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DRAFT FINAL REMEDIALCONSTRUCTION REPORT
AREA SL-4
SALEM ACRES SUPERFUND SITESALEM MA
PREPARED FOR
MASSACHUSETTS ELECTRIC CO25 RESEARCH DRIVE
WESTBOROUGH MA 01582
PREPARED BY
T FORD COMPANY INC118 TENNEY STREET
GEORGETOWN MA 01833
July 181996
Disclaimer This document is a DRAFT document prepared on behalf of the Massachusetts Electric Company under agovernment Consent Decree This document has not undergone formal review by the EPA and DEP The opinionsfindings and conclusions expressed are those of the author and not those of the EPA and DEP
TABLE OF CONTENTS
INTRODUCTION PAGE
1 1 Project Description 1 12 Project Organization 1 1 3 Project Time Line 1 1 4 Project Photos 2
REMEDIAL CONSTRUCTION ACTIVITIES
2 1 Mobilization and Site Preparation 2 2 2 Clearing 4 2 3 Decontamination Dust Control and Health and Safety Monitoring 4 2 4 Excavation and Loading of Fly Ash 5 2 5 Excavation and Loading of Contaminated Overburden 5
and SoilFly Ash Mixture 2 6 Ponded Water 6 2 7 Bedrock Cleaning 6
SITE RESTORATION
3 1 Random Fill 7 3 2 Loam and Seed 7 3 3 FencingDemobilization 8
QUANTITY SURVEYS AND AS-BUILT PLANS
41 Fly Ash Quantity Survey 8 42 Limits of Remediation 9 4 3 Final As-Built 9
TABLES FIGURES PHOTOS
Appendix A - Analytical Results for Ponded Water Appendix B - Quantity Survey Documentation Appendix C - Health and Safety Phase-Out Report
1 INTRODUCTION
11 Project Description
This project consisted of the excavation and removal of fly ash soilfly ash mixtures and contaminated overburden from the SL-4 Area of the Salem Acres Superfund site The work was performed in accordance with the Draft Final Remedial Action Work Plan prepared by T Ford Company Inc (TFCI) dated September 7 1995 and the Draft Final Technical Specifications for Remedial Action of SL-4 Area prepared by GEI Consultants Inc dated June 15 1995
12 Project Organization
TFCI performed the remedial site work under contract to Massachusetts Electric Co (MEC) The following organizations were involved in remediation of SL-4
ORGANIZATION
Massachusetts Electric Co
T Ford Company Inc
GEI Consultants
Cashins amp Associates
KR Rezendes
Turnkey Recycling and Environmental Enterprises
T F Moran
Clark Hydroseeding
Wood Trucking
D amp H Loam
South Essex Sewerage District (SESD)
B amp B Pest Control
ROLE
PRP
General Contractor for site work
Supervising contractor and Sampling Analysis work-subcontractor to MEC
Health amp Safety subcontractor to TFCI
Hauling and disposal of Fly Ash - subcontractor to MEC
Hauling and disposal of Fly AshSoil Mixtures and Contaminated Overburden
Field surveying and quantity estimates Sub to TFCI
Hydroseed restored areas Sub to TFCI
Furnish random fill Sub to TFCI
Furnish loam Sub to TFCI
Disposal of ponded water
Pest control services
13 Project Time Line
MEC issued a Notice to Proceed to TFCI on July 21 1995 TFCI prepared the Draft
Final Remedial Action Work Plan and submitted it to MEC on September 7 1995
The following summarizes milestones for the project
TASK BATES
Mobilization Septembers 1995
Site Preparation September 5 -8 1995
Excavation of Fly Ash September 8 - October 19 1995
Excavation of Contaminated October 18 - December 7 1995 Overburden and Fly AshSoil Mixtures
Bedrock Cleaning November 9 - December 5 1995
Placement of Random Fill November 16 - December 7 1995
Pumping amp Disposal of Ponded November 27 -30 1995 Water
Winter Shutdown December 8 1995 - May 2 1996
Placement of Loam Jute Mat May 2- 101996
Seeding May 14 1996
As-Built Survey May 21 1996
14 Project Photos
Photographs were taken during construction to document the work Representative photographs are included in this report Pre-construction photographs and a videotape were submitted prior to the start of work
2 REMEDIAL CONSTRUCTION ACTIVITIES
21 Mobilization and Site Preparation
TFCI mobilized the following equipment for this project
Cat 950 Front End Loader Komatsu PC 150 Excavator Komatsu PC 200 Excavator Cat D4H Dozer 1000 Gal Sedimentation Tank 9000 Gal Water Supply Tankers (2)
TFCI utilized the site office trailer set-up used by the contractor performing remediation of SL-5 Area (RUST E amp I) TFCI took over the rent and utility charges from DiBiase Realty Trust
The site preparation consisted of constructing a truck loading pad and a decontamination pad improving the access road installation of erosion controls and establishment of work zones
The truck loading pad consisted of a crushed stone area set up along the east side of SL-4 adjacent to the access road A row of concrete Jersey Barriers was set up along the west side of the truck loading pad to contain stockpiled ash and contaminated overburden from spilling on to the pad An excavator was used to load trucks The excavator was able to sit on the stockpiled material behind the Jersey Barriers to load trucks This enabled the operator to carefully load trucks and minimize dust The decontamination pad is discussed in Sec 23
The decontamination pad consisted of an HDPE-lined pad approximately 16 ft wide by 50 ft long The liner was filled with 34 inch crushed stone A sump was constructed to collect rinsate and pump it into a sedimentation tank Heavy timber planks were placed on top of the crushed stone to provide traction for truck tires and prevent rutting of the stone
For dust control TFCI set up a gas-powered high pressure pump capable of 75 gpm at 75 psi The pump fed the network of 2 inch and 1 2 inch flat fire hose with a nozzle for spraying down the work areas
The access road was improved by adding crushed stone as necessary and widening it on both ends of the truck loading and decontamination pads
Erosion controls consisted of silt fence and staked hay bales on the west side of SL-4 adjacent to WA-1 The location of the erosion controls was selected by GEI in conjunction with MADEP and USEPA
The following work zones were established for this site
Exclusion Zone (EZ) Contaminated Reduction Zone (CRZ) Support Zone (SZ)
The limits of these zones were established to conform with the site geometry operational requirements and Health and Safety requirements Initially the EZ was the area within the perimeter boundary of SL-4 except it extended west to the location of the erosion controls The limits of the EZ did not change until all contaminated soil and debris was removed and verified by confirmatory sampling
and testing
The CRZ was established at the top of the slope along the east side of SL-4 The decontamination pad was a major part of the CRZ All worker and equipment decontamination was performed in the CRZ A bootglove washing station was set up in the CRZ along with PPE disposal containers and a handwash PPE was disposed of at Turnkey Landfill in Rochester NH
The Support Zone was established on the east side of the access road opposite SL-4 The office trailer sanitary facilities and water supply were set up in the Support Zone A 2-inch water supply line was temporarily installed under the access road to supply water for decontamination equipment in the CRZ from the water tankers in the SZ
TFCI also initiated a security program to provide full time security watch on site During non-work hours including weekends a security guard was posted in the site trailer The security guard made hourly rounds of the support zone and Access Road including the Barcelona Avenue gate Logs were maintained of security shifts
22 Clearing
Clearing was performed incrementally during the project Trees were cut by chain saw and stockpiled in the Support Zone along the access road Once the majority of trees were cut and stockpiled they were loaded onto 100 cy trailers for off-site disposal Disposal consisted of chipping and burning at a facility in Maine Hauling and disposal was done by Wood Waste of Boston Inc
Phragmites were mixed in with the fly ash during excavation The phragmites constituted a very small portion of the volume of fly ash
23 Decontamination Dust Control and Health and Safety Monitoring
As mentioned above truck loading and decontamination pads were constructed along the east side of the site adjacent to the access road TFCI used a hydraulic excavator to load dump trailers from stockpiles By using an excavator we were able to minimize spillage of material onto the outside of the trailers However all trucks were considered potentially contaminated and were decontaminated by washing down over the decontamination pad
TFCI constructed an overhead spray bar set-up which trucks drove under after loading The wheels and sides of the trucks were then washed down with hoses The decontamination water rinsate was collected in the sump of the HDPE-lined decontamination pad Rinsate was pumped into a 1000 gallon sedimentation tank After removal of the fines the decontamination water was used for dust control
The fly ash was found to be quite dry particularly in the upper 10 to 15 ft and prone to dusting easily TFCI used imported water to keep the fly ash moist in stockpiles and after loading a truck A total of 180000 gallons of water was imported to the site for decontamination and dust control The majority of this water was used for dust control on fly ash The dust control measures employed were quite successful No dust levels were measured exceeding the site criteria at the Barcelona Avenue gate or in the work zones
For Health and Safety Monitoring TFCI contracted with Cashins amp Associates (CA) CA prepared a Health and Safety Plan and performed on-site monitoring of air and noise in the work zone and at the site perimeter A Health and Safety Phase-Out Report prepared by CA is contained in Appendix C
24 Excavation and Loading of Fly Ash
TFCI used two methods for excavating the fly ash and moving it to a stockpile Due to the steep slopes tight quarters and poor traction on the fly ash it was impossible to use a front end loader at the SL-4 site Initially we used an excavator and a bulldozer to excavate and move fly ash to stockpiles
As the mounded area of the fly ash was removed and the excavation began to consist of a steeply sloped face of fly ash we used two excavators The excavators worked as a bucket brigade to excavate and move material up the slope to the stockpile area Material was handled several times to reach the stockpile As the bottom of fly ash level was approached the excavators were able to excavate the fly ash close to the interface between fly ash and contaminated overburden and soilfly ash mixtures
All loading of fly ash was done by an excavator with a large bucket (2 cy capacity) Table 1 summarizes the daily quantities of fly ash loaded In general approximately the same quantity of fly ash was excavated as was loaded each day No significant stockpiles were maintained during the work A stockpile of fly ash excavated on SLshy5 area (by others) was loaded on the first full day of hauling of fly ash from SL-4
25 Excavation and Loading of Contaminated Overburden and SoilFly Ash Mixture
Excavation of contaminated overburden soilfly ash mixture and debris (referred to hereafter as contaminated overburden) was performed using excavators similar to the procedures for fly ash The horizontal limits of excavation were determined by GEI Consultants Inc and are described in the Demonstration of Compliance report prepared by GEI In general the horizontal limits are as follows
Northern - Defined by DA-1 Area Eastern - Defined by confirmatory sampling and analysis along
the Access Road Southern - Defined by SL-5 Area except for Area 1 which was
incorporated into SL-4 site remediation work Western - Defined by WA-1 Area
The bottom of excavation was sampled for confirmatory analysis by GEL The results of this analysis are described in the Demonstration of Compliance Report
Table 2 summarizes the daily quantities of contaminated overburden loaded Approximately the same daily quantity was excavated No significant stockpiles of contaminated overburden were maintained
Where bedrock was encountered contaminated soils were scraped off with the excavator The remaining material was removed as part of bedrock cleaning (see Sec 27) A number of boulders were encountered in the overburden MEC elected to have TFCI decontaminate the boulders on the decontamination pad and then incorporated them into the random fill
26 Ponded Water
Removal of fly ash and contaminated overburden along the western side of SL-4 resulted in a low area which collected both surface water run-off and groundwater seepage This area became a temporary pond containing approximately 100000 to 150000 gallons of water The level fluctuated with the level of the adjoining wetlands
In order to discharge the ponded water to the wetlands (WA-1) the discharge would have to meet Federal drinking water quality standards TFCI arranged for sampling and testing of the ponded water The results are contained in Appendix A Although the water met requirements of USEPA and MADEP for chemical contaminants the water was quite turbid and no practical means of removing suspended solids was available
A request was made to SESD to dispose of the ponded water at its Salem Treatment Facility SESD approved this request on November 20 1995
The ponded water was pumped into conventional septage hauling vehicles on November 27 through 30 1995 A total of 125000 gallons was transported to SESD for disposal Random fill was placed in the low area immediately following pumping of ponded water to avoid collection of additional water
27 Bedrock Cleaning
As required by the Specifications all exposed bedrock was cleaned of all fly ash and
contaminated overburden Several techniques andor methods were used to clean bedrock including
a) Manual broom and shovel work b) Compressor with air gun to loosen material from crevices with water
used for dust control c) A Vac-All truck using water andor compressed air to loosen
material d) A broom attached to the bucket of an excavator
The surface of exposed bedrock was generally quite irregular and required considerable effort to remove soil and fly ash from cracks and crevices In some areas the rock is highly weathered and can be removed In these areas a determination was made in conjunction with GEI as to when to stop removal of weathered bedrock
During placement of random fill and loam some areas of exposed bedrock became re-covered with these earth materials TFCI proposed to topsoil and seed on these areas rather than re-cleaning the bedrock GEI EPA and MEC accepted this proposal
3 SITE RESTORATION
31 Random Fill
Random fill for the site restoration was obtained from a borrow pit located on Munson Street in Peabody MA GEI conducted confirmatory sampling of the borrow source The results are contained in the Demonstration of Compliance Report A grain size analysis is provided in Figure 1 A total of 1176 cy of random fill was delivered to the site and spread over all exposed soil subgrade areas The thickness is 6 inches except along the west side of the site where it ranges up to 5 ft thick where contaminated soil and fly ash were encountered at a deeper level (See Sec 4)
The random fill was spread and compacted using a CAT D4H dozer
32 Loam and Seeding
In the Spring of 1996 after Winter shutdown TFCI placed and spread a 6-inch layer of loam The loam was obtained from a loam stockpile located at a new residential subdivision in Ayer MA called Bennetts Brook and furnished to the site by D amp H Loam Company A total of 695 cy of loam was delivered to the site GEI conducted confirmatory sampling of the loam source The results are contained in the Demonstration of Compliance Report A topsoil analysis report is provided as
Figure 2
The loam was spread using a CAT D4H dozer Areas of the slope where the grade was steeper than 4HIV were first hand-seeded and then covered with Erosion Control and Revegetation Mat (ECRM) The entire loamed area was then hydro-seeded on May 14 1996 The seed used is Massachusetts Highway Department Specification M6030 Slope and Shoulder Mix
33 FencingDemobilization
In order to remove fly ash andor contaminated overburden which extended onto DA-1 it was necessary to remove the fence along the south side of DA-1 After completion of remediation work the fence was replaced Because of the winter shutdown TFCI reinstalled the fence prior to site restoration work to secure the DAshy1 area
Following placement of the random fill TFCI demobilized for winter shutdown Due to an early snowfall it was impossible to loam and seed the site prior to winter shutdown TFCI demobilized equipment and support facilities December 8-13 1995
In the Spring of 1996 it was only necessary to mobilize a dozer and small excavator to place and spread loam
4 QUANTITY SURVEYS AND AS-BUILT PLANS
41 Fly Ash Quantity Survey
In order to calculate the insitu quantity of fly ash for payment TFCI engaged a subcontractor T F Moran for survey work and quantity estimates T F Moran performed an existing conditions topographic survey on April 21 1994 for design studies conducted by GEI Consultants Inc This survey was updated and verified on September 8 1995 by T F Moran for TFCI In addition a stockpile of fly ash removed from SL-5 was also surveyed on this date
T F Moran surveyed the bottom of fly ash on October 18 1995 The results of the fly ash quantity surveys are shown on Figure 3 The quantities of fly ash are as follows
SL-4 Fly Ash 12750 cy SL-5 Fly Ash (stockpiled on SL-4) 520 cv
13270 cy
In addition there was an estimated 1500 cy of fly ash not included in the TF
Moran surveys because the material was in or under active stockpiles at the time of the survey The quantity survey and method of calculation is described in a letter from T F Moran dated January 15 1996 and contained in Appendix B
42 Limits of Remediation
In order to document the limits of remediation T F Moran surveyed the site on November 1 and December 5 1995 Areas where contaminated overburden were removed were surveyed at these times including the limits of exposed bedrock The results of these surveys are shown on Figure 4 The limits of SL-4 site remediation are as follows
Total Site Area Remediated 50860 sf Exposed Ledge 19990 sf
Site Restoration Area 30870 sf
In addition Area 1 is approximately 5416 sf
Note that the total quantity of contaminated overburden and fly ashsoildebris mixture was 6056 tons compared to the estimated 4100 tons from the design studies The primary reasons for the increase include the following
Incorporation of Area 1 from SL-5 in the SL-4 site remediation work
The northern limit of excavation extended further into DA-1 than anticipated in the RA Work Plan
Excavating further west into WA-1 than anticipated in the RA Work Plan
VOC contaminated fly ash and soil in the northwest corner near DAshy1 at a considerable thicknessdepth
The limits of remediation survey are described in the T F Moran letter contained in Appendix B
43 Final As-Built
A final as-built survey was performed by T F Moran on May 21 1996 The results of the survey are shown on Figure 5
TABLE 1 SUMMARY OF ASH REMOVAL
SALEM ACRES SUPERFUND SITE SL-4 AREA
DATE NOMBEraquo0poundLOADS
0AILY TOTAL ifrotfS) i
SEPTS 1 1750
SEPT 1 1 8 13470
SEPT 12 10 21080
SEPT 13 20 45800
SEPT 14 23 50100
SEPT 15 20 43160
SEPT 18 23 46870
SEPT 19 24 54780
SEPT 20 26 52800
SEPT 21 25 47700
SEPT 22 25 46915
SEPT 25 26 51950
SEPT 26 29 56820
SEPT 27 30 55660
SEPT 28 30 58410
SEPT 29 26 53520
OCT2 26 54600
OCT3 26 57000
OCT4 19 41080
OCT5 22 49240
OCT6 26 61860
OCT 10 18 47180
OCT 11 12 33860
OCT 13 17 439 40
OCT 17 3 7600
OCT 19 3 7720
CtnVfOtATIVE TOTAL (TONS)
1750
15220
36300
82100
132200
175360
222230
277010
329810
3775 10
424425
476375
5331 95
5888 55
647265
700785
755385
812385
853465
902705
9645 65
1011745
1045605
1089545
1097145
1104865
TABLE 2 SUMMARY OF CONTAMINATED
OVERBURDEN REMOVAL SALEM ACRES SUPERFUND SITE SL-4 AREA
DATE
on 19 OCT 20
OCT 23
OCT 24
OCT 25
OCT 26
OCT 27
OCT 31
NOV 1
NOV2
NOV 6
NOV 8
NOV 9
NOV 21
NOV 28
DEC 7
NUMBER OF LOADS
14
14
14
13
14
16
18
18
12
4
4
8
8
8
9
2
DAILY TOTAL (TONS)
46121
41649
49314
448 59
46225
48054
62358
56186
491 56
14209
14025
29010
27604
35513
33447
7885
CUMULATIVE TOTAL (TONS)
46121
87770
137084
181943
228168
276222
338580
394766
443922
458131
472156
501166
528770
564283
597730
6056 1 5
- -
--
Oct 17 1995 823PM P02 From LTTS OF Mfl INC PHONE No 617 438 S21S
GRftIN SIZE DISTRIBUTION TEST REPORT C c c e
100 i i ^ i i 7 ^ d bdquo bdquo j laquo ii i A j
bdquo9 bdquo
a 2 - a i
t sh
90 X
N^
B0 raquo m lts
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70 Sk
gtia
Npound G0 shyu
550 gt
UJ bullshy
1u S pound 40 0 ^
30 bull i 20
10
0 2Q 0 1SG 100 10 01 aai 00UL
CRflIM CISC - mm
Test X +3 bull4 GRAVEL bull SflMD bull SILT bull DRY uses LL PI
t 16 00 2Z 3 521 256 SC-SM
SIEVE PERCENT FINCR STEVE PERCENT FINCR Uact on Incrwi nuwtoer ilz ilzi bull flUNSON ST PEABODC
bull bull a 96 3 4 777
15 95 10 714 1 92 e 20 607 Descr pt ion
075 90 40 505 bullSILTY CLAYEY GflNO 0 375 34 50 44 4
100 343
3X1 GRAIN SIZE 200 257
8804D60
gtDia Remarks
xC COEFh 1C1CNT5 UTS OF MASSACHUSETTS INC bull
SS1T to 1 u
Pro jlt-r t No UTS OF naSSACHLKKI lgt IMC Project) CftLCM flCHSCC
5 Richardson Lane
GtoneHam Mft 03 IBB Date 101195 Gamn 1 c- No 44fi1A
Figure 1
From UTS OF Mfl INC PHONE No 517 438 6216 Oct 17 1995 824PM F03
SOT ANALYSIS REPORT FOR NEW LAWN 101195
SOIL AND PLANT TISSUE TESTING LABWEST EXPERIMENT STATIONUNIVERSITY OF MASBACIIUfiFTTr AMHERST MA 01003
LAB NUMBER 3951010-107 BAG NUMBER 23467
DATE BFNT f
SOIL FROM COUNTY SOIL WEIGHT 537 g5cn CROP TURFORASS
UTS OF MASS INC COMMENTS ORGANIC MATTER 6 RICHARDSON LANE STONEHAM MA 02180
SAMPLE ID 4461B
LIMESTONE AND FERTILIZER RECOMMCNDATIONS FOR NEW LAWN CONSTRUCTION
No limestone ia required If peat mooc or similar material ia to be incorporated) see enclosed fact sheet
Fertilizer (per 10OO sq ft) 2 1ba N 2 Ibo P2O5 and O 1 bs KZO
Many fertilizer sources and rates may combine to provide acceptable turfgraes establ iahmont either from seed or aod One or two options baaed on this soil teat follow
Incorporate EITHER a 17-23-6 starter fert111zar at 10 lbs1000 sq ft OR a 30-3-3 lawn fertilizer at 7 1b81000 aq ft plus a 0-45-0 (triple superphosphate) fertilizer at 4 lbs1000 aq ft Hnto the top 3 to 4 inches of soil Retest Bull ona year after turf establishment
PLEASE read the enclosed fact sheets for niora specific Information on fertilization and liming procadurea
SOIL pH 71 NITROGEN NO3-N = Oa ppm NH4-N = 5 ppm BUFFER pH 74 ORGANIC MATTER 72 X (Desirable range 4-10X)
NUTRIENT_LEVELS_PPM_| Low Medium High Very High Phosphorus (P) 8 |XXXXXXXXXXXXX Potaaaium (K) 292 [XXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXX Calcium (Ca) 237S XXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXX Magnesium (Mg) 237 JXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXX
CATION EXCII CAP PERCENT BASE SATURATION MICRONUTRIENT LEVELS 130 Meq100g K= 52 Mg=134 Ca=816 ALL NORMAL
CXTRACTABLE ALUMINUM 41 ppm (Soil ranglaquo 10-250 ppm)
The lead level in thio soil 1s low
COMPUTER PROGRAM5-RECOMMENDATIONRbYOtHIOFPtANT~ampSOILSCI UMASS-AMHERST
Figure 2
TARGET SHEET
THE MATERIAL DESCRIBED BELOW WAS NOT SCANNED BECAUSE
(X) OVERSIZED
() NON-PAPER MEDIA
() OTHER
DESCRIPTION DOC 14732 DRAFT FINAL REMEDIAL CONSTRUCTION REPORT FIGURE 3 TOPOGRAPHIC PLAN SL-4 AREA BOTTOM OF FLY ASH SALEM ACRES SHEET 1 OF 1
THE OMITTED MATERIAL IS AVAILABLE FOR REVIEW BY APPOINTMENT
AT THE EPA NEW ENGLAND SUPERFUND RECORDS CENTER BOSTON MA
TARGET SHEET
THE MATERIAL DESCRIBED BELOW WAS NOT SCANNED BECAUSE
(X) OVERSIZED
() NON-PAPER MEDIA
() OTHER
DESCRIPTION DOC 14732 DRAFT FINAL REMEDIAL CONSTRUCTION REPORT FIGURE 4 TOPOGRAPHIC PLAN SL-4 AREA LIMIT OF REMEDIATION SALEM ACRES SHEET 1OF1
THE OMITTED MATERIAL IS AVAILABLE FOR REVIEW BY APPOINTMENT
AT THE EPA NEW ENGLAND SUPERFUND RECORDS CENTER BOSTON MA
TARGET SHEET
THE MATERIAL DESCRIBED BELOW WAS NOT SCANNED BECAUSE
(X) OVERSIZED
() NON-PAPER MEDIA
() OTHER
DESCRIPTION DOC 14732 DRAFT FINAL REMEDIAL CONSTRUCTION REPORT FIGURE 5 TOPOGRAPHIC PLAN SL-4 AREA AS-BUILT PLAN SALEM ACRES SHEET 1 OF 1
THE OMITTED MATERIAL IS AVAILABLE FOR REVIEW BY APPOINTMENT
AT THE EPA NEW ENGLAND SUPERFUND RECORDS CENTER BOSTON MA
(i)
^mft^m
VIEW OF BARCELONA AVENUE THROUGH ENTRANCE GATE PRECONT RUCTION
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(2)
VIEW OF ACCESS ROAD LOOKING NORTH SL-4 ON LEFT PRECONSTRUCTION
VIEW OF ACCESS ROAD LOOKING NORTH SL-4 ON LEFT DA-1 TO LEFT OF PICKUP TRUCK
PRECONSTRUCTION
(3)
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
O ID a CO z O OHI
CO UJ
OO_l
t CO ii-O
(5)
VIEW OF BOUNDARY BETWEEN SL-4 AND DA-1 LOOKING WEST PRECONSTRUCTION
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(6)
EROSION CONTROLS LOOKING NORTH FROM CORNER OF SL-4SL-5 ADJACENT TO WA-1 PRECONSTRUCTION
(7)
TRUCK LOADING PAD LOOKING NORTHWEST FROM SUPPORT ZONE
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(8)
DECONTAMINATION PAD LOOKING NORTHWEST FROM SUPPORT ZONE
(9)
EXCAVATION OF FLY ASH LOOKING NORTHWEST FROM CRZ NOTE WATER FOR DUST CONTROL
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(10)
VIEW LOOKING WEST AFTER REMOVAL OF FLY ASH NOTE WA-1 BEYOND EROSION CONTROLS
(11)
EXCAVATION OF CONTAMINATED OVERBURDEN LOOKING SOUTH FROM DA-1 BOUNDARY
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(12)
VIEW OF RESTORED SITE LOOKING WEST TOWARD WA-1
0
ltu
wsectbull
D Q
O
O z ^ O O_J LJJ
Q LJJ a o te LJJ
eg 3
(14)
VIEW OF RESTORED SITE LOOKING NORTH TOWARD DA-1 ALONG ACCESS ROAD
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(15)
gtbull bdquobdquo -
VIEW OF RESTORED SITE LOOKING SOUTH TOWARD SL-5
iu O
of bullo
01 u I ltO
w
o B ltabulls to 10
3
I Q Z
O m ^mdash
i sect^^ nu0 (- co^gtW IO - z zilaquo O O 5gl
oLU uj
V) LUo a o LU
(17)
VIEW OF RESTORED SITE ON DA-1 SJDE OF FENCE - LOOKING ST
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(18)
VIEW OF RESTORED SITE ON DA-1 SIDE OF FENCE - LOOKING WEST SL-4 ON RIGHT
APPENDIX A
ANALYTICAL RESULTS FOR
PONDED WATER
110795 1638 copy617 890 3883 TMA-WALTHAM ] 002007
PRELIMINARY REPORT UNAUDITED RESULTS
Thenno Analytical 300 Second Avenue PO Box 521 Waltham HA 02254
Attn Client Services Phone (617) 890-7200
Cashins amp Associates Order S5-11-034 55 Cambridge Street Date 110795 1522 Burlington HA 01803 Work ID Salem Acres Water
Date Received 110295 Attn Bob Cashins Date Completed
Purchase Order NA Invoice Number Client Code CASHINS
SAMPLE IDENTIFICATION
Sample Sample Number Description 01 11019S-924-01A
Sample Number 04
Sample Description
110195-9Z4-01D 02 110195-924-01B 05 110195-924-01E 03 110195-924-01C
Certified By
110795 1638 copy617 890 3883 TMA-WALTHAM 003007
PRELIMINARY REPORT UNAUDITED RESULTS
Order f S5-11-034 Thermo Analytical Page 2 110795 1522 TEST RESULTS BY SAHPLE
Test Description Volatile Organics- Aqueous Method EPA_8240 Test Code Collected 110195 02-00 Category WATER
DATE INJECTED 110695 DILUTION FACTOR 100 All results reported 1n ugL
COMPOUND RESULT DET LIMIT COMPOUND RESULT
Chloromethane U 10 Broroodi chl oromethane U Vinyl Chloride U 10 2-Chloroethyl Vinyl Ether U
Bromxnethane U 10 4-dethyl -2-pentanone U Chloroethane U 10 c1 3-1 3-Di chl oropropene U
Trichlorofluoronwthane U 50 Tol uene U Acetone 17 10 trans-1 3-Di chl oropropene LI
11-Oichloroethene U 50 11 2-Tri chl oroethane J Carbon Dlsulfide U 50 2-Hexanone U
Methyl ene Chloride U 50 Tetrachl oroethene U 12-Oichloroethene (total) U 50 D1 bromochl oromethane U
11-01 Chloroethane U 50 Chlorobenzene U Vinyl Acetate U 10 Ethyl benzene U
2-Butanone U 10 in and p-Xylene U Chloroform U 50 o-Xylene U
111-Tri Chloroethane U 50 Styrene U Carbon Tetrachlortde U 50 Broraoform U
Benzene U 50 112 2-Tat rachl oroethane U 12-01 Chloroethane U 50 1 3-01 chl orobenzene U
Trichloroethene U 50 I 4-Di chl orobenzene U 12-Dichloropropane U 50 12-01 chl orobenzene U
SURROGATE STANDARDS RESULT LEVEL X RECOVERY
12-Dichloroethane-D4 52 50 104 Toluene-08 47 50 94
l-Bromo-4-fluorobenzene 56 50 112
NOTES AND DEFINITIONS FOR THIS REPORT U =bull Undetected at stated detection limit
VOAJI
OET LIMIT
50 50
10 50 50 50 50 10
5 0 50 5 0 5 0 50 50 50 50 50 50 50 50
110795 1639 copy617 890 3883 TMA-WALTHAM copy004007
PRELIMINARY REPORT UNAUDITED RESULTS
Order t S5-11-034 Thermo Analytical Page 4 110795 1522 TEST RESULTS BY SAMPLE
ianple Description 110195-924-010 Lab No 04A Test Description RCRA Metals 1n Water Method SW846 Test Code
Collected 110195 0200 Category WATER
METAL RESULT DETECTION LIMIT METAL RESULT DETECTION LIMIT
Ag Silver U 10 As Arsenic 870 50
Ba Bar inn B69 10 Pb Lead U 50
Cd Cadmium U 50 Se Sel en1 um Z15 50
Cr Chromi um U 20 Hg Mercury U 020
NOTES AND DEFINITIONS FOR THIS REPORT All results reported in ugL U gt Undetected at stated detection limit
110795 1640 Q617 890 3883 TMA-WALTHAM 0005007
PRELIMINARY REPORT UNAUDITED RESULTS
Order S5-11-034 Thermo Analytical Page 5 110795 1522 REGULAR TEST RESULTS BY TEST
Chemical Oxygen Demand Mlnimun Maximum Method EPA600 4101
Sap Sample Description Result Units Limit Prepared Analyzed By 05A 110195-924-01E 64 bullgL 50 110395 110395 JD
Petroleum Hydrocarbons-H20 Minimum Maximum Method EPA600 4181
Samp Sample Description Result Units Limit Prepared Analyzed By 01A 110195-924-01A 108 mgL 050 110395 110395 JO
110795 1640 reg617 890 3883 TMA-WALTHAM copy006007
PRELIMINARY REPORT UNAUDITED RESULTS
Order I S5-11-034 Therm Analytical Page 6 110795 1522 TEST METHODOLOGIES
USEPA Test Methods for Evaluating Solid Wastes (SUS46 Third Edition) Method 7470 - Preparation of water for Mercury analysis
USEPA Test Methods for Evaluating Solid Vastes (SW846 Third Edition) Method 3010 - Add digestion of aqueous samples and extracts for total metals for analysis by Flame Atomic Absorption Spectroscopy or Inductively Coupled Plasma Spectroscopy
USEPA Test Methods for Evaluating Solid Vastes (SWB46 Third Edition Method 8270 mdash Gas ChroroatographyMass Spectrometry for PAHs
Volatile Organics in Water - Hazardous Substance List
SV846 Method 8240 - Modified
Test Methods for Evaluating Solid Waste SU-846 US EPA Office of Solid Waste and Emergency Response Washington 3rd Edition
Aqueous sanples are analyzed in accordance with Method 8240 using a purge and trap technique followed by 64s ChromatographyMass Spectroscopy
Quality assurance procedures for GCMS Include daily tuning and calibration of the mass spectrometer and the use of surrogate standards in each sample to monitor method performance Quantitatton is performed by the Internal standard method Analysis of blanks duplicate samples and standards are run frequently as further quality assurance procedures
USEPA Test Methods for Evaluating Solid Wastes (SW846 Third Edition) Method 3S10 mdash Separatory Funnel Liquid-Liquid Extraction
EPA-6004-79-020 - Chemical Oxygen Demand - Titrimetric Mid-Level Method 4101
EPA6004-79-020 - Petroleum Hydrocarbons 1n Water Total Recoverable Method 4181 (Spectrophotometric Infrared)
110795 1641 copy617 890 3883 TMA-WALTHAM copy007007
APPENDIX B
QUANTITY SURVEY DOCUMENTATION
TFMORAN INC Surveying - Engineering - Land Planning SoilsWetlands Mapping - Landscape Architecture
January 15 1996
Mr Jack Enos Vice President TFord Company Inc 118 Tenney Street Georgetown MA 01833
RE Survey Results - Salem Acres - SL4 Area Salem Massachusetts
Dear Jack
This letter amends the letter of December 13 1995 per our review last week
TFMoran Inc performed topographic surveys at the Salem Acres site on April 21 1994 for GEI Consultants prior to removal of material and for TFord Company on October 18 1995 after the removal of material The survey data from the original survey in 1994 was adjusted thirty feet higher to correct for a datum difference from current site datum This was due to the original reporting of the Site Benchmark (TP34) elevation as 11464 rather than 14464 which is the correct elevation
Once both topographic surfaces were on the site datum the raw cut volume was obtained by Eaglepoint (Volumes Module) Software utilizing the prismoidal method comparing the two surfaces For reference please see the attached topographic plan which superimposes the October 15 1995 contours (dark lines) over the April 21 1994 contours The volume is based on the intersection of the two surfaces Also it was noted that stock piles of material did exist on site which were not surveyed at the time
The final raw cut volume arrived at by the above methods is 12749 Cubic Yards
In November and December of 1995 the site was resurveyed to locate the area of exposed ledge at the site The results of this survey are shown on the attached topographic worksheet dated November 3 1995 and last revised January 15 1996 The results of the survey indicate the total site area to be 50860 sq ft or 117 acres The total area of exposed ledge surveyed is 19990 sq ft or 46 acres If you have any questions regarding the above call me directly Thank you
Sincerely
John W Myhaver Jr ^_ Field Operations Manager
Enclosure ItorLltr
Route 101 Bedford NH 03110 Phone (603) 472-4488 FAX (603) 472-9747
APPENDIX C
HEALTH AND SAFETY PHASE-OUT REPORT
HEALTH AND SAFETY PHASE-OUT REPORT SALEM ACRES SL-4 AREA
Introduction
During remediation work on SL-4 Health and Safety Monitoring was performed Cashins amp Associates Inc of Reading MA performed the following work as a subcontractor to TFCI
1) Preparation of a site-specific Health and Safety Plan (dated September 1 1995)
2) Provide a Field TechnicianIndustrial Hygienist to serve as Site Safety and Health Officer (SSHO) and to conduct air and noise monitoring
3) Provide a Certified Industrial Hygienist to review Health and Safety and to conduct site specific training (record of training included at end of Appendix C)
4) Collect 8-hour air samples for worker exposure and ambient air at the Barcelona Avenue gate Arrange for analysis of the samples and report results
5) Prepare daily and weekly Health and Safety reports
6) Prepare a Health and Safety Phase-Out Report
In general the following health and safety practices were followed
1) All workers wore hard hats safety glasses work boots gloves and hearing protection as minimum level PPE
2) When working in the exclusion zone workers wore in addition to above tyvek rubber overboots and rubber coated gloves When dust was a potential concern an industrial grade dustmist mask was also worn This level of PPE was considered Level D modified
3) Workers leaving the exclusion zone removed PPE (tyveks gloves boots and masks) in the support zone and either disposed of the items or decontaminated them
4) Workers andor visitors without 40-hour OSHA training were not permitted to enter the exclusion zone
Attached is a report prepared by Cashins amp Associates along with weekly Health and Safety Summary Reports prepared by the Field Hygienist In summary the air monitoring results indicate no levels exceeding the applicable exposure guidelines except one instance
During excavation of contaminated overburden in the northwest comer of the site an area of VOC contaminated soil was encountered Total VOCs levels measured using a PID exceeded the action level established in the Health and Safety Plan The SSHO advised TFCI to upgrade to Level C PPE in order to backfill the excavation in this area TFCI equipment operator upgraded and backfilled the area The SSHO in consultation with the Cashins CIH advised TFCI to avoid work in this area until the contaminants were characterized GEI sampled the material for waste characterization analysis and provided the results to TFCI Based on the results an action level was established by the CIH for the specific contaminants found Further PID measurements indicated levels below the new action level and work was resumed
The noise monitoring indicated that the noise level at the Barcelona Avenue gate was not exceeded Only one instance of excess noise level in the work zone was recorded (10 db(a) above the ambient noise level or 85 db(a)) Workers wore hearing protection in this instance
mdash 07171996 1601 6179444032 CASHIMS S ASSOCIATES PAGE 02
CASHINS amp Associates Inc
ItxhalrM Hy-gifnr A Invtronmtnltl Tttling
July 17 1996
Mr Jack Enos T Ford Company Inc USTenney Street Georgetown MA 01833
Dear Jack
The Site Safety and Health Officer (SSHO) from Cashing amp Associates Inc performed daily inspections of the SL-4 area Salem Acres Superfund Site between 9595 and 12195 in accordance with the Health amp Safety Plan (HSP) for the site Daily inspection logs were submitted every day No accidentsincidents were reported during the work period
In accordance with the Health amp Safety Plan the SSHO performed daily air and noise monitoring at the site during Ac project Samples were collected for metals (lead beryllium chromium arsenic) and Polynuclear Aromatic Hydrocarbons (PAHs) at the site perimeter and for workers exposure determination Coal Tar Pitch Volatiles (a benzene soluble extractables) were also used to determine the workers exposure to PAH compounds Coal Tar Pitch Volatiles (CTPV) were analyzed using OSHA 58 Method If CTPV levels oq personal samples exceed the site criteria of 02 ragm3 the sample was submitted for PAHs analysis All air samples on the site perimeter were analyzed for PAH compounds
Site monitoring air sample collection and results report were done under the supervision of a Certified Industrial Hygienist
Full shift personal worker exposure samples were collected once a week Ambient air samples were collected at the Barcelona Avenue gate about 20 feet to the west of the site gate to determine if site contaminants were migrating off site The ambient air samples were also collected once a week during the project except on rainy days and days without work with contaminated soil
All air samples were analyzed by the American Industrial Hygiene Association accredited ESA Laboratories Inc using the following methods PAHs - NIOSH 5515 Lead - NIOSH 7082 Beryllium - NIOSH 7102 Chromium - NIOSH 7024 Arsenic - NIOSH 7900 Coal Tar Pitch Volatiles - OSHA 58 All methods used are accepted by the industrial hygiene community for 8-hour exposure assessment EPA methods are usually used for ambient air measurements
CRErORTTFOmiOO
80 Mam Street bull Reading MA 01867 bull Phone- 61 7-944-4060 bull Fax 61 7-944-4082
07171996 1601 6179444032 CASHIMS amp ASSOCIATES PAGE 03
The results of air samples for metals and PAHs are presented in Table No 1
All concentrations of metals and PAHs at the site perimeter (Barcelona Avenue) and active work zones were below the OSHA Permissible Exposure Limits (PEL) and the American Conference of Governmental Industrial Hygicnists Threshold Limit Value (ACGIH TLV) Two personal samples collected on October 19 and October 23rd showed Coal Tar Pitch Volatiles (CTPV) results above OSHA PEL and AIHA TLV limits Both samples were resubmittcd to the lab for further analysis to determine if PAH compounds are present because the CTPV results were above site criteria
The results of the PAH concentrations for the personal sample on Mark Goodwin on October 19 1995 during excavation and washing trucks and for the personal sample on Ron Maker on October 23 1995 during excavating and cleaning rocks by compressed air were below OSHA PEL and ACGIH TLV limits
The SSHO performed noise monitoring according to the HSP at the exclusion zone and at the Barcelona Avenue site perimeter fence A Dupont sound level meter was used for noise monitoring The noise level in the exclusion zone during all operations except one did not exceed the on site criteria of 85 dB(a) During a short time when the air compressor had been used to clean rocks the sound level in the exclusion zone next to the air compressor did exceed 85 dB(a) Ear protection devices were worn by the workers during that operation At no time did the noise level at the Barcelona Avenue site perimeter exceed 10 dB(a) above the ambient noise level or 85 dB(a)
The SSHO performed total dust monitoring on a daily basis during the project at the site perimeter downwind of work location and at the site gate using a Miniram real time dust meter The summary of dust monitoring is presented in Table No 2 Total dust concentrations on site and off site did not exceed site criteria of 1 mgm3 and the action level of 05 nigny1
The summary of air monitoring for Volatile Organic Compounds (VOC) is presented in Table No 3 VOC concentrations in the working area did not exceed the on site criteria of 5 ppm in a breathing zone VOC concentrations on the site perimeter did not exceed real time off site criteria of 2 ppm
Five detail reports with results of air sampling were submitted during the project period
Sincerely Cashins amp Associates Inc
Evelina Vaughan Industrial Hygieflfst
CASHINS amp ASSOCIATES Inc
80 Mam Street bull Reading MA 01867 bull Phone61 7-944-4060 bull Fax 617-944-4082
07171996 1601 6179444082 CASHINS S ASSOCIATES PAGE 04
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CASHINS amp Associates inc
Ifxtuitral Hygltne A fnvironmtnltt Tuning
W3SXLY HBALTH amp SAFETY PLAN COMPLIANCE SUMMARY R3PORT
CLIENT T foyd C o m a n
LOCATION gal era Acres Sx^perfund Site 8L-4 Area
DATES INCLUDED IN SUMMARY
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09111995 1023 6172739084 CASHINS ASSOCIATES PAGE 01
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WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
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LOCATION Salen Acres Suoerfund Site SL-4 Area
DATES INCLUDED IN SUMMARY
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Industrial Hygitnf amp CmimnmenUl Tinting
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Compan
LOCATION Salem Acres Superfund Site SL-4 Area
DATES INCLUDED IN SUMMARY
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WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
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LOCATION Salem Acres Superfund Site SL-4 Area
DATES INCLUDED IN SUMMARY J_
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THE PURPOSE OF THE FOLLOWING STATEMENT IS TO DOCUMENT THE EXISTENCE OF A CONDITION OR CONCERN WHICH CASHINS amp ASSOCIATES INC BELIEVES WARRANTS IMMEDIATE CORRECTIVE ACTION POSSIBLE SOLUTIONS AND OR CORRECTIVE ACTIONS WILL BE INCLUDED IN THIS NOTIFICATION WHEN POSSIBLE THIS NOTIFICATION IS LIMITED TO SITUATIONS THAT REPRESENT EITHER IMMEDIATE DANGER TO LIFE OR HEALTH CONDITIONS OR PREVIOUSLY IDENTIFIED CHRONIC PROBLEMS THAT UNDERMINE OUR ABILITY TO EFFECTIVELY INSURE COMPLIANCE WITH THE REQUIREMENTS OF THE HEALTH AND SAFETY PLAN
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LOCATION Salem Acres Superfund Site SL-4 Area
DATES INCLUDED IN SUMMARY T
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CASHINS amp Associates Inc
WBBKLY HEALTH amp SAFETY FLAK COMPLIANCE SUMMARY REPORT
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- barcode 14732
- barcodetext SEMS Doc ID 14732
![Page 2: SALEM ACRES SUPERFUND SITE SALEM, MA ...The truck loading pa d consisted of a crushed stone are sea t up along the east sid e o f SL-4 adjacent to the access road A. row of concrete](https://reader036.vdocuments.us/reader036/viewer/2022070114/60729b840fec4e6b4d136a16/html5/thumbnails/2.jpg)
TABLE OF CONTENTS
INTRODUCTION PAGE
1 1 Project Description 1 12 Project Organization 1 1 3 Project Time Line 1 1 4 Project Photos 2
REMEDIAL CONSTRUCTION ACTIVITIES
2 1 Mobilization and Site Preparation 2 2 2 Clearing 4 2 3 Decontamination Dust Control and Health and Safety Monitoring 4 2 4 Excavation and Loading of Fly Ash 5 2 5 Excavation and Loading of Contaminated Overburden 5
and SoilFly Ash Mixture 2 6 Ponded Water 6 2 7 Bedrock Cleaning 6
SITE RESTORATION
3 1 Random Fill 7 3 2 Loam and Seed 7 3 3 FencingDemobilization 8
QUANTITY SURVEYS AND AS-BUILT PLANS
41 Fly Ash Quantity Survey 8 42 Limits of Remediation 9 4 3 Final As-Built 9
TABLES FIGURES PHOTOS
Appendix A - Analytical Results for Ponded Water Appendix B - Quantity Survey Documentation Appendix C - Health and Safety Phase-Out Report
1 INTRODUCTION
11 Project Description
This project consisted of the excavation and removal of fly ash soilfly ash mixtures and contaminated overburden from the SL-4 Area of the Salem Acres Superfund site The work was performed in accordance with the Draft Final Remedial Action Work Plan prepared by T Ford Company Inc (TFCI) dated September 7 1995 and the Draft Final Technical Specifications for Remedial Action of SL-4 Area prepared by GEI Consultants Inc dated June 15 1995
12 Project Organization
TFCI performed the remedial site work under contract to Massachusetts Electric Co (MEC) The following organizations were involved in remediation of SL-4
ORGANIZATION
Massachusetts Electric Co
T Ford Company Inc
GEI Consultants
Cashins amp Associates
KR Rezendes
Turnkey Recycling and Environmental Enterprises
T F Moran
Clark Hydroseeding
Wood Trucking
D amp H Loam
South Essex Sewerage District (SESD)
B amp B Pest Control
ROLE
PRP
General Contractor for site work
Supervising contractor and Sampling Analysis work-subcontractor to MEC
Health amp Safety subcontractor to TFCI
Hauling and disposal of Fly Ash - subcontractor to MEC
Hauling and disposal of Fly AshSoil Mixtures and Contaminated Overburden
Field surveying and quantity estimates Sub to TFCI
Hydroseed restored areas Sub to TFCI
Furnish random fill Sub to TFCI
Furnish loam Sub to TFCI
Disposal of ponded water
Pest control services
13 Project Time Line
MEC issued a Notice to Proceed to TFCI on July 21 1995 TFCI prepared the Draft
Final Remedial Action Work Plan and submitted it to MEC on September 7 1995
The following summarizes milestones for the project
TASK BATES
Mobilization Septembers 1995
Site Preparation September 5 -8 1995
Excavation of Fly Ash September 8 - October 19 1995
Excavation of Contaminated October 18 - December 7 1995 Overburden and Fly AshSoil Mixtures
Bedrock Cleaning November 9 - December 5 1995
Placement of Random Fill November 16 - December 7 1995
Pumping amp Disposal of Ponded November 27 -30 1995 Water
Winter Shutdown December 8 1995 - May 2 1996
Placement of Loam Jute Mat May 2- 101996
Seeding May 14 1996
As-Built Survey May 21 1996
14 Project Photos
Photographs were taken during construction to document the work Representative photographs are included in this report Pre-construction photographs and a videotape were submitted prior to the start of work
2 REMEDIAL CONSTRUCTION ACTIVITIES
21 Mobilization and Site Preparation
TFCI mobilized the following equipment for this project
Cat 950 Front End Loader Komatsu PC 150 Excavator Komatsu PC 200 Excavator Cat D4H Dozer 1000 Gal Sedimentation Tank 9000 Gal Water Supply Tankers (2)
TFCI utilized the site office trailer set-up used by the contractor performing remediation of SL-5 Area (RUST E amp I) TFCI took over the rent and utility charges from DiBiase Realty Trust
The site preparation consisted of constructing a truck loading pad and a decontamination pad improving the access road installation of erosion controls and establishment of work zones
The truck loading pad consisted of a crushed stone area set up along the east side of SL-4 adjacent to the access road A row of concrete Jersey Barriers was set up along the west side of the truck loading pad to contain stockpiled ash and contaminated overburden from spilling on to the pad An excavator was used to load trucks The excavator was able to sit on the stockpiled material behind the Jersey Barriers to load trucks This enabled the operator to carefully load trucks and minimize dust The decontamination pad is discussed in Sec 23
The decontamination pad consisted of an HDPE-lined pad approximately 16 ft wide by 50 ft long The liner was filled with 34 inch crushed stone A sump was constructed to collect rinsate and pump it into a sedimentation tank Heavy timber planks were placed on top of the crushed stone to provide traction for truck tires and prevent rutting of the stone
For dust control TFCI set up a gas-powered high pressure pump capable of 75 gpm at 75 psi The pump fed the network of 2 inch and 1 2 inch flat fire hose with a nozzle for spraying down the work areas
The access road was improved by adding crushed stone as necessary and widening it on both ends of the truck loading and decontamination pads
Erosion controls consisted of silt fence and staked hay bales on the west side of SL-4 adjacent to WA-1 The location of the erosion controls was selected by GEI in conjunction with MADEP and USEPA
The following work zones were established for this site
Exclusion Zone (EZ) Contaminated Reduction Zone (CRZ) Support Zone (SZ)
The limits of these zones were established to conform with the site geometry operational requirements and Health and Safety requirements Initially the EZ was the area within the perimeter boundary of SL-4 except it extended west to the location of the erosion controls The limits of the EZ did not change until all contaminated soil and debris was removed and verified by confirmatory sampling
and testing
The CRZ was established at the top of the slope along the east side of SL-4 The decontamination pad was a major part of the CRZ All worker and equipment decontamination was performed in the CRZ A bootglove washing station was set up in the CRZ along with PPE disposal containers and a handwash PPE was disposed of at Turnkey Landfill in Rochester NH
The Support Zone was established on the east side of the access road opposite SL-4 The office trailer sanitary facilities and water supply were set up in the Support Zone A 2-inch water supply line was temporarily installed under the access road to supply water for decontamination equipment in the CRZ from the water tankers in the SZ
TFCI also initiated a security program to provide full time security watch on site During non-work hours including weekends a security guard was posted in the site trailer The security guard made hourly rounds of the support zone and Access Road including the Barcelona Avenue gate Logs were maintained of security shifts
22 Clearing
Clearing was performed incrementally during the project Trees were cut by chain saw and stockpiled in the Support Zone along the access road Once the majority of trees were cut and stockpiled they were loaded onto 100 cy trailers for off-site disposal Disposal consisted of chipping and burning at a facility in Maine Hauling and disposal was done by Wood Waste of Boston Inc
Phragmites were mixed in with the fly ash during excavation The phragmites constituted a very small portion of the volume of fly ash
23 Decontamination Dust Control and Health and Safety Monitoring
As mentioned above truck loading and decontamination pads were constructed along the east side of the site adjacent to the access road TFCI used a hydraulic excavator to load dump trailers from stockpiles By using an excavator we were able to minimize spillage of material onto the outside of the trailers However all trucks were considered potentially contaminated and were decontaminated by washing down over the decontamination pad
TFCI constructed an overhead spray bar set-up which trucks drove under after loading The wheels and sides of the trucks were then washed down with hoses The decontamination water rinsate was collected in the sump of the HDPE-lined decontamination pad Rinsate was pumped into a 1000 gallon sedimentation tank After removal of the fines the decontamination water was used for dust control
The fly ash was found to be quite dry particularly in the upper 10 to 15 ft and prone to dusting easily TFCI used imported water to keep the fly ash moist in stockpiles and after loading a truck A total of 180000 gallons of water was imported to the site for decontamination and dust control The majority of this water was used for dust control on fly ash The dust control measures employed were quite successful No dust levels were measured exceeding the site criteria at the Barcelona Avenue gate or in the work zones
For Health and Safety Monitoring TFCI contracted with Cashins amp Associates (CA) CA prepared a Health and Safety Plan and performed on-site monitoring of air and noise in the work zone and at the site perimeter A Health and Safety Phase-Out Report prepared by CA is contained in Appendix C
24 Excavation and Loading of Fly Ash
TFCI used two methods for excavating the fly ash and moving it to a stockpile Due to the steep slopes tight quarters and poor traction on the fly ash it was impossible to use a front end loader at the SL-4 site Initially we used an excavator and a bulldozer to excavate and move fly ash to stockpiles
As the mounded area of the fly ash was removed and the excavation began to consist of a steeply sloped face of fly ash we used two excavators The excavators worked as a bucket brigade to excavate and move material up the slope to the stockpile area Material was handled several times to reach the stockpile As the bottom of fly ash level was approached the excavators were able to excavate the fly ash close to the interface between fly ash and contaminated overburden and soilfly ash mixtures
All loading of fly ash was done by an excavator with a large bucket (2 cy capacity) Table 1 summarizes the daily quantities of fly ash loaded In general approximately the same quantity of fly ash was excavated as was loaded each day No significant stockpiles were maintained during the work A stockpile of fly ash excavated on SLshy5 area (by others) was loaded on the first full day of hauling of fly ash from SL-4
25 Excavation and Loading of Contaminated Overburden and SoilFly Ash Mixture
Excavation of contaminated overburden soilfly ash mixture and debris (referred to hereafter as contaminated overburden) was performed using excavators similar to the procedures for fly ash The horizontal limits of excavation were determined by GEI Consultants Inc and are described in the Demonstration of Compliance report prepared by GEI In general the horizontal limits are as follows
Northern - Defined by DA-1 Area Eastern - Defined by confirmatory sampling and analysis along
the Access Road Southern - Defined by SL-5 Area except for Area 1 which was
incorporated into SL-4 site remediation work Western - Defined by WA-1 Area
The bottom of excavation was sampled for confirmatory analysis by GEL The results of this analysis are described in the Demonstration of Compliance Report
Table 2 summarizes the daily quantities of contaminated overburden loaded Approximately the same daily quantity was excavated No significant stockpiles of contaminated overburden were maintained
Where bedrock was encountered contaminated soils were scraped off with the excavator The remaining material was removed as part of bedrock cleaning (see Sec 27) A number of boulders were encountered in the overburden MEC elected to have TFCI decontaminate the boulders on the decontamination pad and then incorporated them into the random fill
26 Ponded Water
Removal of fly ash and contaminated overburden along the western side of SL-4 resulted in a low area which collected both surface water run-off and groundwater seepage This area became a temporary pond containing approximately 100000 to 150000 gallons of water The level fluctuated with the level of the adjoining wetlands
In order to discharge the ponded water to the wetlands (WA-1) the discharge would have to meet Federal drinking water quality standards TFCI arranged for sampling and testing of the ponded water The results are contained in Appendix A Although the water met requirements of USEPA and MADEP for chemical contaminants the water was quite turbid and no practical means of removing suspended solids was available
A request was made to SESD to dispose of the ponded water at its Salem Treatment Facility SESD approved this request on November 20 1995
The ponded water was pumped into conventional septage hauling vehicles on November 27 through 30 1995 A total of 125000 gallons was transported to SESD for disposal Random fill was placed in the low area immediately following pumping of ponded water to avoid collection of additional water
27 Bedrock Cleaning
As required by the Specifications all exposed bedrock was cleaned of all fly ash and
contaminated overburden Several techniques andor methods were used to clean bedrock including
a) Manual broom and shovel work b) Compressor with air gun to loosen material from crevices with water
used for dust control c) A Vac-All truck using water andor compressed air to loosen
material d) A broom attached to the bucket of an excavator
The surface of exposed bedrock was generally quite irregular and required considerable effort to remove soil and fly ash from cracks and crevices In some areas the rock is highly weathered and can be removed In these areas a determination was made in conjunction with GEI as to when to stop removal of weathered bedrock
During placement of random fill and loam some areas of exposed bedrock became re-covered with these earth materials TFCI proposed to topsoil and seed on these areas rather than re-cleaning the bedrock GEI EPA and MEC accepted this proposal
3 SITE RESTORATION
31 Random Fill
Random fill for the site restoration was obtained from a borrow pit located on Munson Street in Peabody MA GEI conducted confirmatory sampling of the borrow source The results are contained in the Demonstration of Compliance Report A grain size analysis is provided in Figure 1 A total of 1176 cy of random fill was delivered to the site and spread over all exposed soil subgrade areas The thickness is 6 inches except along the west side of the site where it ranges up to 5 ft thick where contaminated soil and fly ash were encountered at a deeper level (See Sec 4)
The random fill was spread and compacted using a CAT D4H dozer
32 Loam and Seeding
In the Spring of 1996 after Winter shutdown TFCI placed and spread a 6-inch layer of loam The loam was obtained from a loam stockpile located at a new residential subdivision in Ayer MA called Bennetts Brook and furnished to the site by D amp H Loam Company A total of 695 cy of loam was delivered to the site GEI conducted confirmatory sampling of the loam source The results are contained in the Demonstration of Compliance Report A topsoil analysis report is provided as
Figure 2
The loam was spread using a CAT D4H dozer Areas of the slope where the grade was steeper than 4HIV were first hand-seeded and then covered with Erosion Control and Revegetation Mat (ECRM) The entire loamed area was then hydro-seeded on May 14 1996 The seed used is Massachusetts Highway Department Specification M6030 Slope and Shoulder Mix
33 FencingDemobilization
In order to remove fly ash andor contaminated overburden which extended onto DA-1 it was necessary to remove the fence along the south side of DA-1 After completion of remediation work the fence was replaced Because of the winter shutdown TFCI reinstalled the fence prior to site restoration work to secure the DAshy1 area
Following placement of the random fill TFCI demobilized for winter shutdown Due to an early snowfall it was impossible to loam and seed the site prior to winter shutdown TFCI demobilized equipment and support facilities December 8-13 1995
In the Spring of 1996 it was only necessary to mobilize a dozer and small excavator to place and spread loam
4 QUANTITY SURVEYS AND AS-BUILT PLANS
41 Fly Ash Quantity Survey
In order to calculate the insitu quantity of fly ash for payment TFCI engaged a subcontractor T F Moran for survey work and quantity estimates T F Moran performed an existing conditions topographic survey on April 21 1994 for design studies conducted by GEI Consultants Inc This survey was updated and verified on September 8 1995 by T F Moran for TFCI In addition a stockpile of fly ash removed from SL-5 was also surveyed on this date
T F Moran surveyed the bottom of fly ash on October 18 1995 The results of the fly ash quantity surveys are shown on Figure 3 The quantities of fly ash are as follows
SL-4 Fly Ash 12750 cy SL-5 Fly Ash (stockpiled on SL-4) 520 cv
13270 cy
In addition there was an estimated 1500 cy of fly ash not included in the TF
Moran surveys because the material was in or under active stockpiles at the time of the survey The quantity survey and method of calculation is described in a letter from T F Moran dated January 15 1996 and contained in Appendix B
42 Limits of Remediation
In order to document the limits of remediation T F Moran surveyed the site on November 1 and December 5 1995 Areas where contaminated overburden were removed were surveyed at these times including the limits of exposed bedrock The results of these surveys are shown on Figure 4 The limits of SL-4 site remediation are as follows
Total Site Area Remediated 50860 sf Exposed Ledge 19990 sf
Site Restoration Area 30870 sf
In addition Area 1 is approximately 5416 sf
Note that the total quantity of contaminated overburden and fly ashsoildebris mixture was 6056 tons compared to the estimated 4100 tons from the design studies The primary reasons for the increase include the following
Incorporation of Area 1 from SL-5 in the SL-4 site remediation work
The northern limit of excavation extended further into DA-1 than anticipated in the RA Work Plan
Excavating further west into WA-1 than anticipated in the RA Work Plan
VOC contaminated fly ash and soil in the northwest corner near DAshy1 at a considerable thicknessdepth
The limits of remediation survey are described in the T F Moran letter contained in Appendix B
43 Final As-Built
A final as-built survey was performed by T F Moran on May 21 1996 The results of the survey are shown on Figure 5
TABLE 1 SUMMARY OF ASH REMOVAL
SALEM ACRES SUPERFUND SITE SL-4 AREA
DATE NOMBEraquo0poundLOADS
0AILY TOTAL ifrotfS) i
SEPTS 1 1750
SEPT 1 1 8 13470
SEPT 12 10 21080
SEPT 13 20 45800
SEPT 14 23 50100
SEPT 15 20 43160
SEPT 18 23 46870
SEPT 19 24 54780
SEPT 20 26 52800
SEPT 21 25 47700
SEPT 22 25 46915
SEPT 25 26 51950
SEPT 26 29 56820
SEPT 27 30 55660
SEPT 28 30 58410
SEPT 29 26 53520
OCT2 26 54600
OCT3 26 57000
OCT4 19 41080
OCT5 22 49240
OCT6 26 61860
OCT 10 18 47180
OCT 11 12 33860
OCT 13 17 439 40
OCT 17 3 7600
OCT 19 3 7720
CtnVfOtATIVE TOTAL (TONS)
1750
15220
36300
82100
132200
175360
222230
277010
329810
3775 10
424425
476375
5331 95
5888 55
647265
700785
755385
812385
853465
902705
9645 65
1011745
1045605
1089545
1097145
1104865
TABLE 2 SUMMARY OF CONTAMINATED
OVERBURDEN REMOVAL SALEM ACRES SUPERFUND SITE SL-4 AREA
DATE
on 19 OCT 20
OCT 23
OCT 24
OCT 25
OCT 26
OCT 27
OCT 31
NOV 1
NOV2
NOV 6
NOV 8
NOV 9
NOV 21
NOV 28
DEC 7
NUMBER OF LOADS
14
14
14
13
14
16
18
18
12
4
4
8
8
8
9
2
DAILY TOTAL (TONS)
46121
41649
49314
448 59
46225
48054
62358
56186
491 56
14209
14025
29010
27604
35513
33447
7885
CUMULATIVE TOTAL (TONS)
46121
87770
137084
181943
228168
276222
338580
394766
443922
458131
472156
501166
528770
564283
597730
6056 1 5
- -
--
Oct 17 1995 823PM P02 From LTTS OF Mfl INC PHONE No 617 438 S21S
GRftIN SIZE DISTRIBUTION TEST REPORT C c c e
100 i i ^ i i 7 ^ d bdquo bdquo j laquo ii i A j
bdquo9 bdquo
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t sh
90 X
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Npound G0 shyu
550 gt
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1u S pound 40 0 ^
30 bull i 20
10
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CRflIM CISC - mm
Test X +3 bull4 GRAVEL bull SflMD bull SILT bull DRY uses LL PI
t 16 00 2Z 3 521 256 SC-SM
SIEVE PERCENT FINCR STEVE PERCENT FINCR Uact on Incrwi nuwtoer ilz ilzi bull flUNSON ST PEABODC
bull bull a 96 3 4 777
15 95 10 714 1 92 e 20 607 Descr pt ion
075 90 40 505 bullSILTY CLAYEY GflNO 0 375 34 50 44 4
100 343
3X1 GRAIN SIZE 200 257
8804D60
gtDia Remarks
xC COEFh 1C1CNT5 UTS OF MASSACHUSETTS INC bull
SS1T to 1 u
Pro jlt-r t No UTS OF naSSACHLKKI lgt IMC Project) CftLCM flCHSCC
5 Richardson Lane
GtoneHam Mft 03 IBB Date 101195 Gamn 1 c- No 44fi1A
Figure 1
From UTS OF Mfl INC PHONE No 517 438 6216 Oct 17 1995 824PM F03
SOT ANALYSIS REPORT FOR NEW LAWN 101195
SOIL AND PLANT TISSUE TESTING LABWEST EXPERIMENT STATIONUNIVERSITY OF MASBACIIUfiFTTr AMHERST MA 01003
LAB NUMBER 3951010-107 BAG NUMBER 23467
DATE BFNT f
SOIL FROM COUNTY SOIL WEIGHT 537 g5cn CROP TURFORASS
UTS OF MASS INC COMMENTS ORGANIC MATTER 6 RICHARDSON LANE STONEHAM MA 02180
SAMPLE ID 4461B
LIMESTONE AND FERTILIZER RECOMMCNDATIONS FOR NEW LAWN CONSTRUCTION
No limestone ia required If peat mooc or similar material ia to be incorporated) see enclosed fact sheet
Fertilizer (per 10OO sq ft) 2 1ba N 2 Ibo P2O5 and O 1 bs KZO
Many fertilizer sources and rates may combine to provide acceptable turfgraes establ iahmont either from seed or aod One or two options baaed on this soil teat follow
Incorporate EITHER a 17-23-6 starter fert111zar at 10 lbs1000 sq ft OR a 30-3-3 lawn fertilizer at 7 1b81000 aq ft plus a 0-45-0 (triple superphosphate) fertilizer at 4 lbs1000 aq ft Hnto the top 3 to 4 inches of soil Retest Bull ona year after turf establishment
PLEASE read the enclosed fact sheets for niora specific Information on fertilization and liming procadurea
SOIL pH 71 NITROGEN NO3-N = Oa ppm NH4-N = 5 ppm BUFFER pH 74 ORGANIC MATTER 72 X (Desirable range 4-10X)
NUTRIENT_LEVELS_PPM_| Low Medium High Very High Phosphorus (P) 8 |XXXXXXXXXXXXX Potaaaium (K) 292 [XXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXX Calcium (Ca) 237S XXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXX Magnesium (Mg) 237 JXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXX
CATION EXCII CAP PERCENT BASE SATURATION MICRONUTRIENT LEVELS 130 Meq100g K= 52 Mg=134 Ca=816 ALL NORMAL
CXTRACTABLE ALUMINUM 41 ppm (Soil ranglaquo 10-250 ppm)
The lead level in thio soil 1s low
COMPUTER PROGRAM5-RECOMMENDATIONRbYOtHIOFPtANT~ampSOILSCI UMASS-AMHERST
Figure 2
TARGET SHEET
THE MATERIAL DESCRIBED BELOW WAS NOT SCANNED BECAUSE
(X) OVERSIZED
() NON-PAPER MEDIA
() OTHER
DESCRIPTION DOC 14732 DRAFT FINAL REMEDIAL CONSTRUCTION REPORT FIGURE 3 TOPOGRAPHIC PLAN SL-4 AREA BOTTOM OF FLY ASH SALEM ACRES SHEET 1 OF 1
THE OMITTED MATERIAL IS AVAILABLE FOR REVIEW BY APPOINTMENT
AT THE EPA NEW ENGLAND SUPERFUND RECORDS CENTER BOSTON MA
TARGET SHEET
THE MATERIAL DESCRIBED BELOW WAS NOT SCANNED BECAUSE
(X) OVERSIZED
() NON-PAPER MEDIA
() OTHER
DESCRIPTION DOC 14732 DRAFT FINAL REMEDIAL CONSTRUCTION REPORT FIGURE 4 TOPOGRAPHIC PLAN SL-4 AREA LIMIT OF REMEDIATION SALEM ACRES SHEET 1OF1
THE OMITTED MATERIAL IS AVAILABLE FOR REVIEW BY APPOINTMENT
AT THE EPA NEW ENGLAND SUPERFUND RECORDS CENTER BOSTON MA
TARGET SHEET
THE MATERIAL DESCRIBED BELOW WAS NOT SCANNED BECAUSE
(X) OVERSIZED
() NON-PAPER MEDIA
() OTHER
DESCRIPTION DOC 14732 DRAFT FINAL REMEDIAL CONSTRUCTION REPORT FIGURE 5 TOPOGRAPHIC PLAN SL-4 AREA AS-BUILT PLAN SALEM ACRES SHEET 1 OF 1
THE OMITTED MATERIAL IS AVAILABLE FOR REVIEW BY APPOINTMENT
AT THE EPA NEW ENGLAND SUPERFUND RECORDS CENTER BOSTON MA
(i)
^mft^m
VIEW OF BARCELONA AVENUE THROUGH ENTRANCE GATE PRECONT RUCTION
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(2)
VIEW OF ACCESS ROAD LOOKING NORTH SL-4 ON LEFT PRECONSTRUCTION
VIEW OF ACCESS ROAD LOOKING NORTH SL-4 ON LEFT DA-1 TO LEFT OF PICKUP TRUCK
PRECONSTRUCTION
(3)
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
O ID a CO z O OHI
CO UJ
OO_l
t CO ii-O
(5)
VIEW OF BOUNDARY BETWEEN SL-4 AND DA-1 LOOKING WEST PRECONSTRUCTION
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(6)
EROSION CONTROLS LOOKING NORTH FROM CORNER OF SL-4SL-5 ADJACENT TO WA-1 PRECONSTRUCTION
(7)
TRUCK LOADING PAD LOOKING NORTHWEST FROM SUPPORT ZONE
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(8)
DECONTAMINATION PAD LOOKING NORTHWEST FROM SUPPORT ZONE
(9)
EXCAVATION OF FLY ASH LOOKING NORTHWEST FROM CRZ NOTE WATER FOR DUST CONTROL
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(10)
VIEW LOOKING WEST AFTER REMOVAL OF FLY ASH NOTE WA-1 BEYOND EROSION CONTROLS
(11)
EXCAVATION OF CONTAMINATED OVERBURDEN LOOKING SOUTH FROM DA-1 BOUNDARY
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(12)
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APPENDIX A
ANALYTICAL RESULTS FOR
PONDED WATER
110795 1638 copy617 890 3883 TMA-WALTHAM ] 002007
PRELIMINARY REPORT UNAUDITED RESULTS
Thenno Analytical 300 Second Avenue PO Box 521 Waltham HA 02254
Attn Client Services Phone (617) 890-7200
Cashins amp Associates Order S5-11-034 55 Cambridge Street Date 110795 1522 Burlington HA 01803 Work ID Salem Acres Water
Date Received 110295 Attn Bob Cashins Date Completed
Purchase Order NA Invoice Number Client Code CASHINS
SAMPLE IDENTIFICATION
Sample Sample Number Description 01 11019S-924-01A
Sample Number 04
Sample Description
110195-9Z4-01D 02 110195-924-01B 05 110195-924-01E 03 110195-924-01C
Certified By
110795 1638 copy617 890 3883 TMA-WALTHAM 003007
PRELIMINARY REPORT UNAUDITED RESULTS
Order f S5-11-034 Thermo Analytical Page 2 110795 1522 TEST RESULTS BY SAHPLE
Test Description Volatile Organics- Aqueous Method EPA_8240 Test Code Collected 110195 02-00 Category WATER
DATE INJECTED 110695 DILUTION FACTOR 100 All results reported 1n ugL
COMPOUND RESULT DET LIMIT COMPOUND RESULT
Chloromethane U 10 Broroodi chl oromethane U Vinyl Chloride U 10 2-Chloroethyl Vinyl Ether U
Bromxnethane U 10 4-dethyl -2-pentanone U Chloroethane U 10 c1 3-1 3-Di chl oropropene U
Trichlorofluoronwthane U 50 Tol uene U Acetone 17 10 trans-1 3-Di chl oropropene LI
11-Oichloroethene U 50 11 2-Tri chl oroethane J Carbon Dlsulfide U 50 2-Hexanone U
Methyl ene Chloride U 50 Tetrachl oroethene U 12-Oichloroethene (total) U 50 D1 bromochl oromethane U
11-01 Chloroethane U 50 Chlorobenzene U Vinyl Acetate U 10 Ethyl benzene U
2-Butanone U 10 in and p-Xylene U Chloroform U 50 o-Xylene U
111-Tri Chloroethane U 50 Styrene U Carbon Tetrachlortde U 50 Broraoform U
Benzene U 50 112 2-Tat rachl oroethane U 12-01 Chloroethane U 50 1 3-01 chl orobenzene U
Trichloroethene U 50 I 4-Di chl orobenzene U 12-Dichloropropane U 50 12-01 chl orobenzene U
SURROGATE STANDARDS RESULT LEVEL X RECOVERY
12-Dichloroethane-D4 52 50 104 Toluene-08 47 50 94
l-Bromo-4-fluorobenzene 56 50 112
NOTES AND DEFINITIONS FOR THIS REPORT U =bull Undetected at stated detection limit
VOAJI
OET LIMIT
50 50
10 50 50 50 50 10
5 0 50 5 0 5 0 50 50 50 50 50 50 50 50
110795 1639 copy617 890 3883 TMA-WALTHAM copy004007
PRELIMINARY REPORT UNAUDITED RESULTS
Order t S5-11-034 Thermo Analytical Page 4 110795 1522 TEST RESULTS BY SAMPLE
ianple Description 110195-924-010 Lab No 04A Test Description RCRA Metals 1n Water Method SW846 Test Code
Collected 110195 0200 Category WATER
METAL RESULT DETECTION LIMIT METAL RESULT DETECTION LIMIT
Ag Silver U 10 As Arsenic 870 50
Ba Bar inn B69 10 Pb Lead U 50
Cd Cadmium U 50 Se Sel en1 um Z15 50
Cr Chromi um U 20 Hg Mercury U 020
NOTES AND DEFINITIONS FOR THIS REPORT All results reported in ugL U gt Undetected at stated detection limit
110795 1640 Q617 890 3883 TMA-WALTHAM 0005007
PRELIMINARY REPORT UNAUDITED RESULTS
Order S5-11-034 Thermo Analytical Page 5 110795 1522 REGULAR TEST RESULTS BY TEST
Chemical Oxygen Demand Mlnimun Maximum Method EPA600 4101
Sap Sample Description Result Units Limit Prepared Analyzed By 05A 110195-924-01E 64 bullgL 50 110395 110395 JD
Petroleum Hydrocarbons-H20 Minimum Maximum Method EPA600 4181
Samp Sample Description Result Units Limit Prepared Analyzed By 01A 110195-924-01A 108 mgL 050 110395 110395 JO
110795 1640 reg617 890 3883 TMA-WALTHAM copy006007
PRELIMINARY REPORT UNAUDITED RESULTS
Order I S5-11-034 Therm Analytical Page 6 110795 1522 TEST METHODOLOGIES
USEPA Test Methods for Evaluating Solid Wastes (SUS46 Third Edition) Method 7470 - Preparation of water for Mercury analysis
USEPA Test Methods for Evaluating Solid Vastes (SW846 Third Edition) Method 3010 - Add digestion of aqueous samples and extracts for total metals for analysis by Flame Atomic Absorption Spectroscopy or Inductively Coupled Plasma Spectroscopy
USEPA Test Methods for Evaluating Solid Vastes (SWB46 Third Edition Method 8270 mdash Gas ChroroatographyMass Spectrometry for PAHs
Volatile Organics in Water - Hazardous Substance List
SV846 Method 8240 - Modified
Test Methods for Evaluating Solid Waste SU-846 US EPA Office of Solid Waste and Emergency Response Washington 3rd Edition
Aqueous sanples are analyzed in accordance with Method 8240 using a purge and trap technique followed by 64s ChromatographyMass Spectroscopy
Quality assurance procedures for GCMS Include daily tuning and calibration of the mass spectrometer and the use of surrogate standards in each sample to monitor method performance Quantitatton is performed by the Internal standard method Analysis of blanks duplicate samples and standards are run frequently as further quality assurance procedures
USEPA Test Methods for Evaluating Solid Wastes (SW846 Third Edition) Method 3S10 mdash Separatory Funnel Liquid-Liquid Extraction
EPA-6004-79-020 - Chemical Oxygen Demand - Titrimetric Mid-Level Method 4101
EPA6004-79-020 - Petroleum Hydrocarbons 1n Water Total Recoverable Method 4181 (Spectrophotometric Infrared)
110795 1641 copy617 890 3883 TMA-WALTHAM copy007007
APPENDIX B
QUANTITY SURVEY DOCUMENTATION
TFMORAN INC Surveying - Engineering - Land Planning SoilsWetlands Mapping - Landscape Architecture
January 15 1996
Mr Jack Enos Vice President TFord Company Inc 118 Tenney Street Georgetown MA 01833
RE Survey Results - Salem Acres - SL4 Area Salem Massachusetts
Dear Jack
This letter amends the letter of December 13 1995 per our review last week
TFMoran Inc performed topographic surveys at the Salem Acres site on April 21 1994 for GEI Consultants prior to removal of material and for TFord Company on October 18 1995 after the removal of material The survey data from the original survey in 1994 was adjusted thirty feet higher to correct for a datum difference from current site datum This was due to the original reporting of the Site Benchmark (TP34) elevation as 11464 rather than 14464 which is the correct elevation
Once both topographic surfaces were on the site datum the raw cut volume was obtained by Eaglepoint (Volumes Module) Software utilizing the prismoidal method comparing the two surfaces For reference please see the attached topographic plan which superimposes the October 15 1995 contours (dark lines) over the April 21 1994 contours The volume is based on the intersection of the two surfaces Also it was noted that stock piles of material did exist on site which were not surveyed at the time
The final raw cut volume arrived at by the above methods is 12749 Cubic Yards
In November and December of 1995 the site was resurveyed to locate the area of exposed ledge at the site The results of this survey are shown on the attached topographic worksheet dated November 3 1995 and last revised January 15 1996 The results of the survey indicate the total site area to be 50860 sq ft or 117 acres The total area of exposed ledge surveyed is 19990 sq ft or 46 acres If you have any questions regarding the above call me directly Thank you
Sincerely
John W Myhaver Jr ^_ Field Operations Manager
Enclosure ItorLltr
Route 101 Bedford NH 03110 Phone (603) 472-4488 FAX (603) 472-9747
APPENDIX C
HEALTH AND SAFETY PHASE-OUT REPORT
HEALTH AND SAFETY PHASE-OUT REPORT SALEM ACRES SL-4 AREA
Introduction
During remediation work on SL-4 Health and Safety Monitoring was performed Cashins amp Associates Inc of Reading MA performed the following work as a subcontractor to TFCI
1) Preparation of a site-specific Health and Safety Plan (dated September 1 1995)
2) Provide a Field TechnicianIndustrial Hygienist to serve as Site Safety and Health Officer (SSHO) and to conduct air and noise monitoring
3) Provide a Certified Industrial Hygienist to review Health and Safety and to conduct site specific training (record of training included at end of Appendix C)
4) Collect 8-hour air samples for worker exposure and ambient air at the Barcelona Avenue gate Arrange for analysis of the samples and report results
5) Prepare daily and weekly Health and Safety reports
6) Prepare a Health and Safety Phase-Out Report
In general the following health and safety practices were followed
1) All workers wore hard hats safety glasses work boots gloves and hearing protection as minimum level PPE
2) When working in the exclusion zone workers wore in addition to above tyvek rubber overboots and rubber coated gloves When dust was a potential concern an industrial grade dustmist mask was also worn This level of PPE was considered Level D modified
3) Workers leaving the exclusion zone removed PPE (tyveks gloves boots and masks) in the support zone and either disposed of the items or decontaminated them
4) Workers andor visitors without 40-hour OSHA training were not permitted to enter the exclusion zone
Attached is a report prepared by Cashins amp Associates along with weekly Health and Safety Summary Reports prepared by the Field Hygienist In summary the air monitoring results indicate no levels exceeding the applicable exposure guidelines except one instance
During excavation of contaminated overburden in the northwest comer of the site an area of VOC contaminated soil was encountered Total VOCs levels measured using a PID exceeded the action level established in the Health and Safety Plan The SSHO advised TFCI to upgrade to Level C PPE in order to backfill the excavation in this area TFCI equipment operator upgraded and backfilled the area The SSHO in consultation with the Cashins CIH advised TFCI to avoid work in this area until the contaminants were characterized GEI sampled the material for waste characterization analysis and provided the results to TFCI Based on the results an action level was established by the CIH for the specific contaminants found Further PID measurements indicated levels below the new action level and work was resumed
The noise monitoring indicated that the noise level at the Barcelona Avenue gate was not exceeded Only one instance of excess noise level in the work zone was recorded (10 db(a) above the ambient noise level or 85 db(a)) Workers wore hearing protection in this instance
mdash 07171996 1601 6179444032 CASHIMS S ASSOCIATES PAGE 02
CASHINS amp Associates Inc
ItxhalrM Hy-gifnr A Invtronmtnltl Tttling
July 17 1996
Mr Jack Enos T Ford Company Inc USTenney Street Georgetown MA 01833
Dear Jack
The Site Safety and Health Officer (SSHO) from Cashing amp Associates Inc performed daily inspections of the SL-4 area Salem Acres Superfund Site between 9595 and 12195 in accordance with the Health amp Safety Plan (HSP) for the site Daily inspection logs were submitted every day No accidentsincidents were reported during the work period
In accordance with the Health amp Safety Plan the SSHO performed daily air and noise monitoring at the site during Ac project Samples were collected for metals (lead beryllium chromium arsenic) and Polynuclear Aromatic Hydrocarbons (PAHs) at the site perimeter and for workers exposure determination Coal Tar Pitch Volatiles (a benzene soluble extractables) were also used to determine the workers exposure to PAH compounds Coal Tar Pitch Volatiles (CTPV) were analyzed using OSHA 58 Method If CTPV levels oq personal samples exceed the site criteria of 02 ragm3 the sample was submitted for PAHs analysis All air samples on the site perimeter were analyzed for PAH compounds
Site monitoring air sample collection and results report were done under the supervision of a Certified Industrial Hygienist
Full shift personal worker exposure samples were collected once a week Ambient air samples were collected at the Barcelona Avenue gate about 20 feet to the west of the site gate to determine if site contaminants were migrating off site The ambient air samples were also collected once a week during the project except on rainy days and days without work with contaminated soil
All air samples were analyzed by the American Industrial Hygiene Association accredited ESA Laboratories Inc using the following methods PAHs - NIOSH 5515 Lead - NIOSH 7082 Beryllium - NIOSH 7102 Chromium - NIOSH 7024 Arsenic - NIOSH 7900 Coal Tar Pitch Volatiles - OSHA 58 All methods used are accepted by the industrial hygiene community for 8-hour exposure assessment EPA methods are usually used for ambient air measurements
CRErORTTFOmiOO
80 Mam Street bull Reading MA 01867 bull Phone- 61 7-944-4060 bull Fax 61 7-944-4082
07171996 1601 6179444032 CASHIMS amp ASSOCIATES PAGE 03
The results of air samples for metals and PAHs are presented in Table No 1
All concentrations of metals and PAHs at the site perimeter (Barcelona Avenue) and active work zones were below the OSHA Permissible Exposure Limits (PEL) and the American Conference of Governmental Industrial Hygicnists Threshold Limit Value (ACGIH TLV) Two personal samples collected on October 19 and October 23rd showed Coal Tar Pitch Volatiles (CTPV) results above OSHA PEL and AIHA TLV limits Both samples were resubmittcd to the lab for further analysis to determine if PAH compounds are present because the CTPV results were above site criteria
The results of the PAH concentrations for the personal sample on Mark Goodwin on October 19 1995 during excavation and washing trucks and for the personal sample on Ron Maker on October 23 1995 during excavating and cleaning rocks by compressed air were below OSHA PEL and ACGIH TLV limits
The SSHO performed noise monitoring according to the HSP at the exclusion zone and at the Barcelona Avenue site perimeter fence A Dupont sound level meter was used for noise monitoring The noise level in the exclusion zone during all operations except one did not exceed the on site criteria of 85 dB(a) During a short time when the air compressor had been used to clean rocks the sound level in the exclusion zone next to the air compressor did exceed 85 dB(a) Ear protection devices were worn by the workers during that operation At no time did the noise level at the Barcelona Avenue site perimeter exceed 10 dB(a) above the ambient noise level or 85 dB(a)
The SSHO performed total dust monitoring on a daily basis during the project at the site perimeter downwind of work location and at the site gate using a Miniram real time dust meter The summary of dust monitoring is presented in Table No 2 Total dust concentrations on site and off site did not exceed site criteria of 1 mgm3 and the action level of 05 nigny1
The summary of air monitoring for Volatile Organic Compounds (VOC) is presented in Table No 3 VOC concentrations in the working area did not exceed the on site criteria of 5 ppm in a breathing zone VOC concentrations on the site perimeter did not exceed real time off site criteria of 2 ppm
Five detail reports with results of air sampling were submitted during the project period
Sincerely Cashins amp Associates Inc
Evelina Vaughan Industrial Hygieflfst
CASHINS amp ASSOCIATES Inc
80 Mam Street bull Reading MA 01867 bull Phone61 7-944-4060 bull Fax 617-944-4082
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Ifxtuitral Hygltne A fnvironmtnltt Tuning
W3SXLY HBALTH amp SAFETY PLAN COMPLIANCE SUMMARY R3PORT
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DATES INCLUDED IN SUMMARY
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LOCATION Salem Acres Superfund Site SL-4 Area
DATES INCLUDED IN SUMMARY
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LOCATION Salem Acrlaquoa Superfund Site 9L-4 Area
DATES INCLUDED IN SUMMARY
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LOCATION Salem Acres Superfund Site SL-4 Area
DATES INCLUDED IN SUMMARY J_
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LOCATION Salem Acres Superfund Site SL-4 Area
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CASHINS amp Associates Inc
WBBKLY HEALTH amp SAFETY FLAK COMPLIANCE SUMMARY REPORT
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LOCATION i Sal am Acrlaquolaquo Suparfund Sita SL-4 Area
DATES INCLUDED IN SUMMARY i bull pound7 mdash
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- barcode 14732
- barcodetext SEMS Doc ID 14732
![Page 3: SALEM ACRES SUPERFUND SITE SALEM, MA ...The truck loading pa d consisted of a crushed stone are sea t up along the east sid e o f SL-4 adjacent to the access road A. row of concrete](https://reader036.vdocuments.us/reader036/viewer/2022070114/60729b840fec4e6b4d136a16/html5/thumbnails/3.jpg)
1 INTRODUCTION
11 Project Description
This project consisted of the excavation and removal of fly ash soilfly ash mixtures and contaminated overburden from the SL-4 Area of the Salem Acres Superfund site The work was performed in accordance with the Draft Final Remedial Action Work Plan prepared by T Ford Company Inc (TFCI) dated September 7 1995 and the Draft Final Technical Specifications for Remedial Action of SL-4 Area prepared by GEI Consultants Inc dated June 15 1995
12 Project Organization
TFCI performed the remedial site work under contract to Massachusetts Electric Co (MEC) The following organizations were involved in remediation of SL-4
ORGANIZATION
Massachusetts Electric Co
T Ford Company Inc
GEI Consultants
Cashins amp Associates
KR Rezendes
Turnkey Recycling and Environmental Enterprises
T F Moran
Clark Hydroseeding
Wood Trucking
D amp H Loam
South Essex Sewerage District (SESD)
B amp B Pest Control
ROLE
PRP
General Contractor for site work
Supervising contractor and Sampling Analysis work-subcontractor to MEC
Health amp Safety subcontractor to TFCI
Hauling and disposal of Fly Ash - subcontractor to MEC
Hauling and disposal of Fly AshSoil Mixtures and Contaminated Overburden
Field surveying and quantity estimates Sub to TFCI
Hydroseed restored areas Sub to TFCI
Furnish random fill Sub to TFCI
Furnish loam Sub to TFCI
Disposal of ponded water
Pest control services
13 Project Time Line
MEC issued a Notice to Proceed to TFCI on July 21 1995 TFCI prepared the Draft
Final Remedial Action Work Plan and submitted it to MEC on September 7 1995
The following summarizes milestones for the project
TASK BATES
Mobilization Septembers 1995
Site Preparation September 5 -8 1995
Excavation of Fly Ash September 8 - October 19 1995
Excavation of Contaminated October 18 - December 7 1995 Overburden and Fly AshSoil Mixtures
Bedrock Cleaning November 9 - December 5 1995
Placement of Random Fill November 16 - December 7 1995
Pumping amp Disposal of Ponded November 27 -30 1995 Water
Winter Shutdown December 8 1995 - May 2 1996
Placement of Loam Jute Mat May 2- 101996
Seeding May 14 1996
As-Built Survey May 21 1996
14 Project Photos
Photographs were taken during construction to document the work Representative photographs are included in this report Pre-construction photographs and a videotape were submitted prior to the start of work
2 REMEDIAL CONSTRUCTION ACTIVITIES
21 Mobilization and Site Preparation
TFCI mobilized the following equipment for this project
Cat 950 Front End Loader Komatsu PC 150 Excavator Komatsu PC 200 Excavator Cat D4H Dozer 1000 Gal Sedimentation Tank 9000 Gal Water Supply Tankers (2)
TFCI utilized the site office trailer set-up used by the contractor performing remediation of SL-5 Area (RUST E amp I) TFCI took over the rent and utility charges from DiBiase Realty Trust
The site preparation consisted of constructing a truck loading pad and a decontamination pad improving the access road installation of erosion controls and establishment of work zones
The truck loading pad consisted of a crushed stone area set up along the east side of SL-4 adjacent to the access road A row of concrete Jersey Barriers was set up along the west side of the truck loading pad to contain stockpiled ash and contaminated overburden from spilling on to the pad An excavator was used to load trucks The excavator was able to sit on the stockpiled material behind the Jersey Barriers to load trucks This enabled the operator to carefully load trucks and minimize dust The decontamination pad is discussed in Sec 23
The decontamination pad consisted of an HDPE-lined pad approximately 16 ft wide by 50 ft long The liner was filled with 34 inch crushed stone A sump was constructed to collect rinsate and pump it into a sedimentation tank Heavy timber planks were placed on top of the crushed stone to provide traction for truck tires and prevent rutting of the stone
For dust control TFCI set up a gas-powered high pressure pump capable of 75 gpm at 75 psi The pump fed the network of 2 inch and 1 2 inch flat fire hose with a nozzle for spraying down the work areas
The access road was improved by adding crushed stone as necessary and widening it on both ends of the truck loading and decontamination pads
Erosion controls consisted of silt fence and staked hay bales on the west side of SL-4 adjacent to WA-1 The location of the erosion controls was selected by GEI in conjunction with MADEP and USEPA
The following work zones were established for this site
Exclusion Zone (EZ) Contaminated Reduction Zone (CRZ) Support Zone (SZ)
The limits of these zones were established to conform with the site geometry operational requirements and Health and Safety requirements Initially the EZ was the area within the perimeter boundary of SL-4 except it extended west to the location of the erosion controls The limits of the EZ did not change until all contaminated soil and debris was removed and verified by confirmatory sampling
and testing
The CRZ was established at the top of the slope along the east side of SL-4 The decontamination pad was a major part of the CRZ All worker and equipment decontamination was performed in the CRZ A bootglove washing station was set up in the CRZ along with PPE disposal containers and a handwash PPE was disposed of at Turnkey Landfill in Rochester NH
The Support Zone was established on the east side of the access road opposite SL-4 The office trailer sanitary facilities and water supply were set up in the Support Zone A 2-inch water supply line was temporarily installed under the access road to supply water for decontamination equipment in the CRZ from the water tankers in the SZ
TFCI also initiated a security program to provide full time security watch on site During non-work hours including weekends a security guard was posted in the site trailer The security guard made hourly rounds of the support zone and Access Road including the Barcelona Avenue gate Logs were maintained of security shifts
22 Clearing
Clearing was performed incrementally during the project Trees were cut by chain saw and stockpiled in the Support Zone along the access road Once the majority of trees were cut and stockpiled they were loaded onto 100 cy trailers for off-site disposal Disposal consisted of chipping and burning at a facility in Maine Hauling and disposal was done by Wood Waste of Boston Inc
Phragmites were mixed in with the fly ash during excavation The phragmites constituted a very small portion of the volume of fly ash
23 Decontamination Dust Control and Health and Safety Monitoring
As mentioned above truck loading and decontamination pads were constructed along the east side of the site adjacent to the access road TFCI used a hydraulic excavator to load dump trailers from stockpiles By using an excavator we were able to minimize spillage of material onto the outside of the trailers However all trucks were considered potentially contaminated and were decontaminated by washing down over the decontamination pad
TFCI constructed an overhead spray bar set-up which trucks drove under after loading The wheels and sides of the trucks were then washed down with hoses The decontamination water rinsate was collected in the sump of the HDPE-lined decontamination pad Rinsate was pumped into a 1000 gallon sedimentation tank After removal of the fines the decontamination water was used for dust control
The fly ash was found to be quite dry particularly in the upper 10 to 15 ft and prone to dusting easily TFCI used imported water to keep the fly ash moist in stockpiles and after loading a truck A total of 180000 gallons of water was imported to the site for decontamination and dust control The majority of this water was used for dust control on fly ash The dust control measures employed were quite successful No dust levels were measured exceeding the site criteria at the Barcelona Avenue gate or in the work zones
For Health and Safety Monitoring TFCI contracted with Cashins amp Associates (CA) CA prepared a Health and Safety Plan and performed on-site monitoring of air and noise in the work zone and at the site perimeter A Health and Safety Phase-Out Report prepared by CA is contained in Appendix C
24 Excavation and Loading of Fly Ash
TFCI used two methods for excavating the fly ash and moving it to a stockpile Due to the steep slopes tight quarters and poor traction on the fly ash it was impossible to use a front end loader at the SL-4 site Initially we used an excavator and a bulldozer to excavate and move fly ash to stockpiles
As the mounded area of the fly ash was removed and the excavation began to consist of a steeply sloped face of fly ash we used two excavators The excavators worked as a bucket brigade to excavate and move material up the slope to the stockpile area Material was handled several times to reach the stockpile As the bottom of fly ash level was approached the excavators were able to excavate the fly ash close to the interface between fly ash and contaminated overburden and soilfly ash mixtures
All loading of fly ash was done by an excavator with a large bucket (2 cy capacity) Table 1 summarizes the daily quantities of fly ash loaded In general approximately the same quantity of fly ash was excavated as was loaded each day No significant stockpiles were maintained during the work A stockpile of fly ash excavated on SLshy5 area (by others) was loaded on the first full day of hauling of fly ash from SL-4
25 Excavation and Loading of Contaminated Overburden and SoilFly Ash Mixture
Excavation of contaminated overburden soilfly ash mixture and debris (referred to hereafter as contaminated overburden) was performed using excavators similar to the procedures for fly ash The horizontal limits of excavation were determined by GEI Consultants Inc and are described in the Demonstration of Compliance report prepared by GEI In general the horizontal limits are as follows
Northern - Defined by DA-1 Area Eastern - Defined by confirmatory sampling and analysis along
the Access Road Southern - Defined by SL-5 Area except for Area 1 which was
incorporated into SL-4 site remediation work Western - Defined by WA-1 Area
The bottom of excavation was sampled for confirmatory analysis by GEL The results of this analysis are described in the Demonstration of Compliance Report
Table 2 summarizes the daily quantities of contaminated overburden loaded Approximately the same daily quantity was excavated No significant stockpiles of contaminated overburden were maintained
Where bedrock was encountered contaminated soils were scraped off with the excavator The remaining material was removed as part of bedrock cleaning (see Sec 27) A number of boulders were encountered in the overburden MEC elected to have TFCI decontaminate the boulders on the decontamination pad and then incorporated them into the random fill
26 Ponded Water
Removal of fly ash and contaminated overburden along the western side of SL-4 resulted in a low area which collected both surface water run-off and groundwater seepage This area became a temporary pond containing approximately 100000 to 150000 gallons of water The level fluctuated with the level of the adjoining wetlands
In order to discharge the ponded water to the wetlands (WA-1) the discharge would have to meet Federal drinking water quality standards TFCI arranged for sampling and testing of the ponded water The results are contained in Appendix A Although the water met requirements of USEPA and MADEP for chemical contaminants the water was quite turbid and no practical means of removing suspended solids was available
A request was made to SESD to dispose of the ponded water at its Salem Treatment Facility SESD approved this request on November 20 1995
The ponded water was pumped into conventional septage hauling vehicles on November 27 through 30 1995 A total of 125000 gallons was transported to SESD for disposal Random fill was placed in the low area immediately following pumping of ponded water to avoid collection of additional water
27 Bedrock Cleaning
As required by the Specifications all exposed bedrock was cleaned of all fly ash and
contaminated overburden Several techniques andor methods were used to clean bedrock including
a) Manual broom and shovel work b) Compressor with air gun to loosen material from crevices with water
used for dust control c) A Vac-All truck using water andor compressed air to loosen
material d) A broom attached to the bucket of an excavator
The surface of exposed bedrock was generally quite irregular and required considerable effort to remove soil and fly ash from cracks and crevices In some areas the rock is highly weathered and can be removed In these areas a determination was made in conjunction with GEI as to when to stop removal of weathered bedrock
During placement of random fill and loam some areas of exposed bedrock became re-covered with these earth materials TFCI proposed to topsoil and seed on these areas rather than re-cleaning the bedrock GEI EPA and MEC accepted this proposal
3 SITE RESTORATION
31 Random Fill
Random fill for the site restoration was obtained from a borrow pit located on Munson Street in Peabody MA GEI conducted confirmatory sampling of the borrow source The results are contained in the Demonstration of Compliance Report A grain size analysis is provided in Figure 1 A total of 1176 cy of random fill was delivered to the site and spread over all exposed soil subgrade areas The thickness is 6 inches except along the west side of the site where it ranges up to 5 ft thick where contaminated soil and fly ash were encountered at a deeper level (See Sec 4)
The random fill was spread and compacted using a CAT D4H dozer
32 Loam and Seeding
In the Spring of 1996 after Winter shutdown TFCI placed and spread a 6-inch layer of loam The loam was obtained from a loam stockpile located at a new residential subdivision in Ayer MA called Bennetts Brook and furnished to the site by D amp H Loam Company A total of 695 cy of loam was delivered to the site GEI conducted confirmatory sampling of the loam source The results are contained in the Demonstration of Compliance Report A topsoil analysis report is provided as
Figure 2
The loam was spread using a CAT D4H dozer Areas of the slope where the grade was steeper than 4HIV were first hand-seeded and then covered with Erosion Control and Revegetation Mat (ECRM) The entire loamed area was then hydro-seeded on May 14 1996 The seed used is Massachusetts Highway Department Specification M6030 Slope and Shoulder Mix
33 FencingDemobilization
In order to remove fly ash andor contaminated overburden which extended onto DA-1 it was necessary to remove the fence along the south side of DA-1 After completion of remediation work the fence was replaced Because of the winter shutdown TFCI reinstalled the fence prior to site restoration work to secure the DAshy1 area
Following placement of the random fill TFCI demobilized for winter shutdown Due to an early snowfall it was impossible to loam and seed the site prior to winter shutdown TFCI demobilized equipment and support facilities December 8-13 1995
In the Spring of 1996 it was only necessary to mobilize a dozer and small excavator to place and spread loam
4 QUANTITY SURVEYS AND AS-BUILT PLANS
41 Fly Ash Quantity Survey
In order to calculate the insitu quantity of fly ash for payment TFCI engaged a subcontractor T F Moran for survey work and quantity estimates T F Moran performed an existing conditions topographic survey on April 21 1994 for design studies conducted by GEI Consultants Inc This survey was updated and verified on September 8 1995 by T F Moran for TFCI In addition a stockpile of fly ash removed from SL-5 was also surveyed on this date
T F Moran surveyed the bottom of fly ash on October 18 1995 The results of the fly ash quantity surveys are shown on Figure 3 The quantities of fly ash are as follows
SL-4 Fly Ash 12750 cy SL-5 Fly Ash (stockpiled on SL-4) 520 cv
13270 cy
In addition there was an estimated 1500 cy of fly ash not included in the TF
Moran surveys because the material was in or under active stockpiles at the time of the survey The quantity survey and method of calculation is described in a letter from T F Moran dated January 15 1996 and contained in Appendix B
42 Limits of Remediation
In order to document the limits of remediation T F Moran surveyed the site on November 1 and December 5 1995 Areas where contaminated overburden were removed were surveyed at these times including the limits of exposed bedrock The results of these surveys are shown on Figure 4 The limits of SL-4 site remediation are as follows
Total Site Area Remediated 50860 sf Exposed Ledge 19990 sf
Site Restoration Area 30870 sf
In addition Area 1 is approximately 5416 sf
Note that the total quantity of contaminated overburden and fly ashsoildebris mixture was 6056 tons compared to the estimated 4100 tons from the design studies The primary reasons for the increase include the following
Incorporation of Area 1 from SL-5 in the SL-4 site remediation work
The northern limit of excavation extended further into DA-1 than anticipated in the RA Work Plan
Excavating further west into WA-1 than anticipated in the RA Work Plan
VOC contaminated fly ash and soil in the northwest corner near DAshy1 at a considerable thicknessdepth
The limits of remediation survey are described in the T F Moran letter contained in Appendix B
43 Final As-Built
A final as-built survey was performed by T F Moran on May 21 1996 The results of the survey are shown on Figure 5
TABLE 1 SUMMARY OF ASH REMOVAL
SALEM ACRES SUPERFUND SITE SL-4 AREA
DATE NOMBEraquo0poundLOADS
0AILY TOTAL ifrotfS) i
SEPTS 1 1750
SEPT 1 1 8 13470
SEPT 12 10 21080
SEPT 13 20 45800
SEPT 14 23 50100
SEPT 15 20 43160
SEPT 18 23 46870
SEPT 19 24 54780
SEPT 20 26 52800
SEPT 21 25 47700
SEPT 22 25 46915
SEPT 25 26 51950
SEPT 26 29 56820
SEPT 27 30 55660
SEPT 28 30 58410
SEPT 29 26 53520
OCT2 26 54600
OCT3 26 57000
OCT4 19 41080
OCT5 22 49240
OCT6 26 61860
OCT 10 18 47180
OCT 11 12 33860
OCT 13 17 439 40
OCT 17 3 7600
OCT 19 3 7720
CtnVfOtATIVE TOTAL (TONS)
1750
15220
36300
82100
132200
175360
222230
277010
329810
3775 10
424425
476375
5331 95
5888 55
647265
700785
755385
812385
853465
902705
9645 65
1011745
1045605
1089545
1097145
1104865
TABLE 2 SUMMARY OF CONTAMINATED
OVERBURDEN REMOVAL SALEM ACRES SUPERFUND SITE SL-4 AREA
DATE
on 19 OCT 20
OCT 23
OCT 24
OCT 25
OCT 26
OCT 27
OCT 31
NOV 1
NOV2
NOV 6
NOV 8
NOV 9
NOV 21
NOV 28
DEC 7
NUMBER OF LOADS
14
14
14
13
14
16
18
18
12
4
4
8
8
8
9
2
DAILY TOTAL (TONS)
46121
41649
49314
448 59
46225
48054
62358
56186
491 56
14209
14025
29010
27604
35513
33447
7885
CUMULATIVE TOTAL (TONS)
46121
87770
137084
181943
228168
276222
338580
394766
443922
458131
472156
501166
528770
564283
597730
6056 1 5
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Oct 17 1995 823PM P02 From LTTS OF Mfl INC PHONE No 617 438 S21S
GRftIN SIZE DISTRIBUTION TEST REPORT C c c e
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Test X +3 bull4 GRAVEL bull SflMD bull SILT bull DRY uses LL PI
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SIEVE PERCENT FINCR STEVE PERCENT FINCR Uact on Incrwi nuwtoer ilz ilzi bull flUNSON ST PEABODC
bull bull a 96 3 4 777
15 95 10 714 1 92 e 20 607 Descr pt ion
075 90 40 505 bullSILTY CLAYEY GflNO 0 375 34 50 44 4
100 343
3X1 GRAIN SIZE 200 257
8804D60
gtDia Remarks
xC COEFh 1C1CNT5 UTS OF MASSACHUSETTS INC bull
SS1T to 1 u
Pro jlt-r t No UTS OF naSSACHLKKI lgt IMC Project) CftLCM flCHSCC
5 Richardson Lane
GtoneHam Mft 03 IBB Date 101195 Gamn 1 c- No 44fi1A
Figure 1
From UTS OF Mfl INC PHONE No 517 438 6216 Oct 17 1995 824PM F03
SOT ANALYSIS REPORT FOR NEW LAWN 101195
SOIL AND PLANT TISSUE TESTING LABWEST EXPERIMENT STATIONUNIVERSITY OF MASBACIIUfiFTTr AMHERST MA 01003
LAB NUMBER 3951010-107 BAG NUMBER 23467
DATE BFNT f
SOIL FROM COUNTY SOIL WEIGHT 537 g5cn CROP TURFORASS
UTS OF MASS INC COMMENTS ORGANIC MATTER 6 RICHARDSON LANE STONEHAM MA 02180
SAMPLE ID 4461B
LIMESTONE AND FERTILIZER RECOMMCNDATIONS FOR NEW LAWN CONSTRUCTION
No limestone ia required If peat mooc or similar material ia to be incorporated) see enclosed fact sheet
Fertilizer (per 10OO sq ft) 2 1ba N 2 Ibo P2O5 and O 1 bs KZO
Many fertilizer sources and rates may combine to provide acceptable turfgraes establ iahmont either from seed or aod One or two options baaed on this soil teat follow
Incorporate EITHER a 17-23-6 starter fert111zar at 10 lbs1000 sq ft OR a 30-3-3 lawn fertilizer at 7 1b81000 aq ft plus a 0-45-0 (triple superphosphate) fertilizer at 4 lbs1000 aq ft Hnto the top 3 to 4 inches of soil Retest Bull ona year after turf establishment
PLEASE read the enclosed fact sheets for niora specific Information on fertilization and liming procadurea
SOIL pH 71 NITROGEN NO3-N = Oa ppm NH4-N = 5 ppm BUFFER pH 74 ORGANIC MATTER 72 X (Desirable range 4-10X)
NUTRIENT_LEVELS_PPM_| Low Medium High Very High Phosphorus (P) 8 |XXXXXXXXXXXXX Potaaaium (K) 292 [XXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXX Calcium (Ca) 237S XXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXX Magnesium (Mg) 237 JXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXX
CATION EXCII CAP PERCENT BASE SATURATION MICRONUTRIENT LEVELS 130 Meq100g K= 52 Mg=134 Ca=816 ALL NORMAL
CXTRACTABLE ALUMINUM 41 ppm (Soil ranglaquo 10-250 ppm)
The lead level in thio soil 1s low
COMPUTER PROGRAM5-RECOMMENDATIONRbYOtHIOFPtANT~ampSOILSCI UMASS-AMHERST
Figure 2
TARGET SHEET
THE MATERIAL DESCRIBED BELOW WAS NOT SCANNED BECAUSE
(X) OVERSIZED
() NON-PAPER MEDIA
() OTHER
DESCRIPTION DOC 14732 DRAFT FINAL REMEDIAL CONSTRUCTION REPORT FIGURE 3 TOPOGRAPHIC PLAN SL-4 AREA BOTTOM OF FLY ASH SALEM ACRES SHEET 1 OF 1
THE OMITTED MATERIAL IS AVAILABLE FOR REVIEW BY APPOINTMENT
AT THE EPA NEW ENGLAND SUPERFUND RECORDS CENTER BOSTON MA
TARGET SHEET
THE MATERIAL DESCRIBED BELOW WAS NOT SCANNED BECAUSE
(X) OVERSIZED
() NON-PAPER MEDIA
() OTHER
DESCRIPTION DOC 14732 DRAFT FINAL REMEDIAL CONSTRUCTION REPORT FIGURE 4 TOPOGRAPHIC PLAN SL-4 AREA LIMIT OF REMEDIATION SALEM ACRES SHEET 1OF1
THE OMITTED MATERIAL IS AVAILABLE FOR REVIEW BY APPOINTMENT
AT THE EPA NEW ENGLAND SUPERFUND RECORDS CENTER BOSTON MA
TARGET SHEET
THE MATERIAL DESCRIBED BELOW WAS NOT SCANNED BECAUSE
(X) OVERSIZED
() NON-PAPER MEDIA
() OTHER
DESCRIPTION DOC 14732 DRAFT FINAL REMEDIAL CONSTRUCTION REPORT FIGURE 5 TOPOGRAPHIC PLAN SL-4 AREA AS-BUILT PLAN SALEM ACRES SHEET 1 OF 1
THE OMITTED MATERIAL IS AVAILABLE FOR REVIEW BY APPOINTMENT
AT THE EPA NEW ENGLAND SUPERFUND RECORDS CENTER BOSTON MA
(i)
^mft^m
VIEW OF BARCELONA AVENUE THROUGH ENTRANCE GATE PRECONT RUCTION
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(2)
VIEW OF ACCESS ROAD LOOKING NORTH SL-4 ON LEFT PRECONSTRUCTION
VIEW OF ACCESS ROAD LOOKING NORTH SL-4 ON LEFT DA-1 TO LEFT OF PICKUP TRUCK
PRECONSTRUCTION
(3)
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
O ID a CO z O OHI
CO UJ
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(5)
VIEW OF BOUNDARY BETWEEN SL-4 AND DA-1 LOOKING WEST PRECONSTRUCTION
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(6)
EROSION CONTROLS LOOKING NORTH FROM CORNER OF SL-4SL-5 ADJACENT TO WA-1 PRECONSTRUCTION
(7)
TRUCK LOADING PAD LOOKING NORTHWEST FROM SUPPORT ZONE
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(8)
DECONTAMINATION PAD LOOKING NORTHWEST FROM SUPPORT ZONE
(9)
EXCAVATION OF FLY ASH LOOKING NORTHWEST FROM CRZ NOTE WATER FOR DUST CONTROL
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(10)
VIEW LOOKING WEST AFTER REMOVAL OF FLY ASH NOTE WA-1 BEYOND EROSION CONTROLS
(11)
EXCAVATION OF CONTAMINATED OVERBURDEN LOOKING SOUTH FROM DA-1 BOUNDARY
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(12)
VIEW OF RESTORED SITE LOOKING WEST TOWARD WA-1
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VIEW OF RESTORED SITE LOOKING NORTH TOWARD DA-1 ALONG ACCESS ROAD
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(15)
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VIEW OF RESTORED SITE ON DA-1 SJDE OF FENCE - LOOKING ST
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(18)
VIEW OF RESTORED SITE ON DA-1 SIDE OF FENCE - LOOKING WEST SL-4 ON RIGHT
APPENDIX A
ANALYTICAL RESULTS FOR
PONDED WATER
110795 1638 copy617 890 3883 TMA-WALTHAM ] 002007
PRELIMINARY REPORT UNAUDITED RESULTS
Thenno Analytical 300 Second Avenue PO Box 521 Waltham HA 02254
Attn Client Services Phone (617) 890-7200
Cashins amp Associates Order S5-11-034 55 Cambridge Street Date 110795 1522 Burlington HA 01803 Work ID Salem Acres Water
Date Received 110295 Attn Bob Cashins Date Completed
Purchase Order NA Invoice Number Client Code CASHINS
SAMPLE IDENTIFICATION
Sample Sample Number Description 01 11019S-924-01A
Sample Number 04
Sample Description
110195-9Z4-01D 02 110195-924-01B 05 110195-924-01E 03 110195-924-01C
Certified By
110795 1638 copy617 890 3883 TMA-WALTHAM 003007
PRELIMINARY REPORT UNAUDITED RESULTS
Order f S5-11-034 Thermo Analytical Page 2 110795 1522 TEST RESULTS BY SAHPLE
Test Description Volatile Organics- Aqueous Method EPA_8240 Test Code Collected 110195 02-00 Category WATER
DATE INJECTED 110695 DILUTION FACTOR 100 All results reported 1n ugL
COMPOUND RESULT DET LIMIT COMPOUND RESULT
Chloromethane U 10 Broroodi chl oromethane U Vinyl Chloride U 10 2-Chloroethyl Vinyl Ether U
Bromxnethane U 10 4-dethyl -2-pentanone U Chloroethane U 10 c1 3-1 3-Di chl oropropene U
Trichlorofluoronwthane U 50 Tol uene U Acetone 17 10 trans-1 3-Di chl oropropene LI
11-Oichloroethene U 50 11 2-Tri chl oroethane J Carbon Dlsulfide U 50 2-Hexanone U
Methyl ene Chloride U 50 Tetrachl oroethene U 12-Oichloroethene (total) U 50 D1 bromochl oromethane U
11-01 Chloroethane U 50 Chlorobenzene U Vinyl Acetate U 10 Ethyl benzene U
2-Butanone U 10 in and p-Xylene U Chloroform U 50 o-Xylene U
111-Tri Chloroethane U 50 Styrene U Carbon Tetrachlortde U 50 Broraoform U
Benzene U 50 112 2-Tat rachl oroethane U 12-01 Chloroethane U 50 1 3-01 chl orobenzene U
Trichloroethene U 50 I 4-Di chl orobenzene U 12-Dichloropropane U 50 12-01 chl orobenzene U
SURROGATE STANDARDS RESULT LEVEL X RECOVERY
12-Dichloroethane-D4 52 50 104 Toluene-08 47 50 94
l-Bromo-4-fluorobenzene 56 50 112
NOTES AND DEFINITIONS FOR THIS REPORT U =bull Undetected at stated detection limit
VOAJI
OET LIMIT
50 50
10 50 50 50 50 10
5 0 50 5 0 5 0 50 50 50 50 50 50 50 50
110795 1639 copy617 890 3883 TMA-WALTHAM copy004007
PRELIMINARY REPORT UNAUDITED RESULTS
Order t S5-11-034 Thermo Analytical Page 4 110795 1522 TEST RESULTS BY SAMPLE
ianple Description 110195-924-010 Lab No 04A Test Description RCRA Metals 1n Water Method SW846 Test Code
Collected 110195 0200 Category WATER
METAL RESULT DETECTION LIMIT METAL RESULT DETECTION LIMIT
Ag Silver U 10 As Arsenic 870 50
Ba Bar inn B69 10 Pb Lead U 50
Cd Cadmium U 50 Se Sel en1 um Z15 50
Cr Chromi um U 20 Hg Mercury U 020
NOTES AND DEFINITIONS FOR THIS REPORT All results reported in ugL U gt Undetected at stated detection limit
110795 1640 Q617 890 3883 TMA-WALTHAM 0005007
PRELIMINARY REPORT UNAUDITED RESULTS
Order S5-11-034 Thermo Analytical Page 5 110795 1522 REGULAR TEST RESULTS BY TEST
Chemical Oxygen Demand Mlnimun Maximum Method EPA600 4101
Sap Sample Description Result Units Limit Prepared Analyzed By 05A 110195-924-01E 64 bullgL 50 110395 110395 JD
Petroleum Hydrocarbons-H20 Minimum Maximum Method EPA600 4181
Samp Sample Description Result Units Limit Prepared Analyzed By 01A 110195-924-01A 108 mgL 050 110395 110395 JO
110795 1640 reg617 890 3883 TMA-WALTHAM copy006007
PRELIMINARY REPORT UNAUDITED RESULTS
Order I S5-11-034 Therm Analytical Page 6 110795 1522 TEST METHODOLOGIES
USEPA Test Methods for Evaluating Solid Wastes (SUS46 Third Edition) Method 7470 - Preparation of water for Mercury analysis
USEPA Test Methods for Evaluating Solid Vastes (SW846 Third Edition) Method 3010 - Add digestion of aqueous samples and extracts for total metals for analysis by Flame Atomic Absorption Spectroscopy or Inductively Coupled Plasma Spectroscopy
USEPA Test Methods for Evaluating Solid Vastes (SWB46 Third Edition Method 8270 mdash Gas ChroroatographyMass Spectrometry for PAHs
Volatile Organics in Water - Hazardous Substance List
SV846 Method 8240 - Modified
Test Methods for Evaluating Solid Waste SU-846 US EPA Office of Solid Waste and Emergency Response Washington 3rd Edition
Aqueous sanples are analyzed in accordance with Method 8240 using a purge and trap technique followed by 64s ChromatographyMass Spectroscopy
Quality assurance procedures for GCMS Include daily tuning and calibration of the mass spectrometer and the use of surrogate standards in each sample to monitor method performance Quantitatton is performed by the Internal standard method Analysis of blanks duplicate samples and standards are run frequently as further quality assurance procedures
USEPA Test Methods for Evaluating Solid Wastes (SW846 Third Edition) Method 3S10 mdash Separatory Funnel Liquid-Liquid Extraction
EPA-6004-79-020 - Chemical Oxygen Demand - Titrimetric Mid-Level Method 4101
EPA6004-79-020 - Petroleum Hydrocarbons 1n Water Total Recoverable Method 4181 (Spectrophotometric Infrared)
110795 1641 copy617 890 3883 TMA-WALTHAM copy007007
APPENDIX B
QUANTITY SURVEY DOCUMENTATION
TFMORAN INC Surveying - Engineering - Land Planning SoilsWetlands Mapping - Landscape Architecture
January 15 1996
Mr Jack Enos Vice President TFord Company Inc 118 Tenney Street Georgetown MA 01833
RE Survey Results - Salem Acres - SL4 Area Salem Massachusetts
Dear Jack
This letter amends the letter of December 13 1995 per our review last week
TFMoran Inc performed topographic surveys at the Salem Acres site on April 21 1994 for GEI Consultants prior to removal of material and for TFord Company on October 18 1995 after the removal of material The survey data from the original survey in 1994 was adjusted thirty feet higher to correct for a datum difference from current site datum This was due to the original reporting of the Site Benchmark (TP34) elevation as 11464 rather than 14464 which is the correct elevation
Once both topographic surfaces were on the site datum the raw cut volume was obtained by Eaglepoint (Volumes Module) Software utilizing the prismoidal method comparing the two surfaces For reference please see the attached topographic plan which superimposes the October 15 1995 contours (dark lines) over the April 21 1994 contours The volume is based on the intersection of the two surfaces Also it was noted that stock piles of material did exist on site which were not surveyed at the time
The final raw cut volume arrived at by the above methods is 12749 Cubic Yards
In November and December of 1995 the site was resurveyed to locate the area of exposed ledge at the site The results of this survey are shown on the attached topographic worksheet dated November 3 1995 and last revised January 15 1996 The results of the survey indicate the total site area to be 50860 sq ft or 117 acres The total area of exposed ledge surveyed is 19990 sq ft or 46 acres If you have any questions regarding the above call me directly Thank you
Sincerely
John W Myhaver Jr ^_ Field Operations Manager
Enclosure ItorLltr
Route 101 Bedford NH 03110 Phone (603) 472-4488 FAX (603) 472-9747
APPENDIX C
HEALTH AND SAFETY PHASE-OUT REPORT
HEALTH AND SAFETY PHASE-OUT REPORT SALEM ACRES SL-4 AREA
Introduction
During remediation work on SL-4 Health and Safety Monitoring was performed Cashins amp Associates Inc of Reading MA performed the following work as a subcontractor to TFCI
1) Preparation of a site-specific Health and Safety Plan (dated September 1 1995)
2) Provide a Field TechnicianIndustrial Hygienist to serve as Site Safety and Health Officer (SSHO) and to conduct air and noise monitoring
3) Provide a Certified Industrial Hygienist to review Health and Safety and to conduct site specific training (record of training included at end of Appendix C)
4) Collect 8-hour air samples for worker exposure and ambient air at the Barcelona Avenue gate Arrange for analysis of the samples and report results
5) Prepare daily and weekly Health and Safety reports
6) Prepare a Health and Safety Phase-Out Report
In general the following health and safety practices were followed
1) All workers wore hard hats safety glasses work boots gloves and hearing protection as minimum level PPE
2) When working in the exclusion zone workers wore in addition to above tyvek rubber overboots and rubber coated gloves When dust was a potential concern an industrial grade dustmist mask was also worn This level of PPE was considered Level D modified
3) Workers leaving the exclusion zone removed PPE (tyveks gloves boots and masks) in the support zone and either disposed of the items or decontaminated them
4) Workers andor visitors without 40-hour OSHA training were not permitted to enter the exclusion zone
Attached is a report prepared by Cashins amp Associates along with weekly Health and Safety Summary Reports prepared by the Field Hygienist In summary the air monitoring results indicate no levels exceeding the applicable exposure guidelines except one instance
During excavation of contaminated overburden in the northwest comer of the site an area of VOC contaminated soil was encountered Total VOCs levels measured using a PID exceeded the action level established in the Health and Safety Plan The SSHO advised TFCI to upgrade to Level C PPE in order to backfill the excavation in this area TFCI equipment operator upgraded and backfilled the area The SSHO in consultation with the Cashins CIH advised TFCI to avoid work in this area until the contaminants were characterized GEI sampled the material for waste characterization analysis and provided the results to TFCI Based on the results an action level was established by the CIH for the specific contaminants found Further PID measurements indicated levels below the new action level and work was resumed
The noise monitoring indicated that the noise level at the Barcelona Avenue gate was not exceeded Only one instance of excess noise level in the work zone was recorded (10 db(a) above the ambient noise level or 85 db(a)) Workers wore hearing protection in this instance
mdash 07171996 1601 6179444032 CASHIMS S ASSOCIATES PAGE 02
CASHINS amp Associates Inc
ItxhalrM Hy-gifnr A Invtronmtnltl Tttling
July 17 1996
Mr Jack Enos T Ford Company Inc USTenney Street Georgetown MA 01833
Dear Jack
The Site Safety and Health Officer (SSHO) from Cashing amp Associates Inc performed daily inspections of the SL-4 area Salem Acres Superfund Site between 9595 and 12195 in accordance with the Health amp Safety Plan (HSP) for the site Daily inspection logs were submitted every day No accidentsincidents were reported during the work period
In accordance with the Health amp Safety Plan the SSHO performed daily air and noise monitoring at the site during Ac project Samples were collected for metals (lead beryllium chromium arsenic) and Polynuclear Aromatic Hydrocarbons (PAHs) at the site perimeter and for workers exposure determination Coal Tar Pitch Volatiles (a benzene soluble extractables) were also used to determine the workers exposure to PAH compounds Coal Tar Pitch Volatiles (CTPV) were analyzed using OSHA 58 Method If CTPV levels oq personal samples exceed the site criteria of 02 ragm3 the sample was submitted for PAHs analysis All air samples on the site perimeter were analyzed for PAH compounds
Site monitoring air sample collection and results report were done under the supervision of a Certified Industrial Hygienist
Full shift personal worker exposure samples were collected once a week Ambient air samples were collected at the Barcelona Avenue gate about 20 feet to the west of the site gate to determine if site contaminants were migrating off site The ambient air samples were also collected once a week during the project except on rainy days and days without work with contaminated soil
All air samples were analyzed by the American Industrial Hygiene Association accredited ESA Laboratories Inc using the following methods PAHs - NIOSH 5515 Lead - NIOSH 7082 Beryllium - NIOSH 7102 Chromium - NIOSH 7024 Arsenic - NIOSH 7900 Coal Tar Pitch Volatiles - OSHA 58 All methods used are accepted by the industrial hygiene community for 8-hour exposure assessment EPA methods are usually used for ambient air measurements
CRErORTTFOmiOO
80 Mam Street bull Reading MA 01867 bull Phone- 61 7-944-4060 bull Fax 61 7-944-4082
07171996 1601 6179444032 CASHIMS amp ASSOCIATES PAGE 03
The results of air samples for metals and PAHs are presented in Table No 1
All concentrations of metals and PAHs at the site perimeter (Barcelona Avenue) and active work zones were below the OSHA Permissible Exposure Limits (PEL) and the American Conference of Governmental Industrial Hygicnists Threshold Limit Value (ACGIH TLV) Two personal samples collected on October 19 and October 23rd showed Coal Tar Pitch Volatiles (CTPV) results above OSHA PEL and AIHA TLV limits Both samples were resubmittcd to the lab for further analysis to determine if PAH compounds are present because the CTPV results were above site criteria
The results of the PAH concentrations for the personal sample on Mark Goodwin on October 19 1995 during excavation and washing trucks and for the personal sample on Ron Maker on October 23 1995 during excavating and cleaning rocks by compressed air were below OSHA PEL and ACGIH TLV limits
The SSHO performed noise monitoring according to the HSP at the exclusion zone and at the Barcelona Avenue site perimeter fence A Dupont sound level meter was used for noise monitoring The noise level in the exclusion zone during all operations except one did not exceed the on site criteria of 85 dB(a) During a short time when the air compressor had been used to clean rocks the sound level in the exclusion zone next to the air compressor did exceed 85 dB(a) Ear protection devices were worn by the workers during that operation At no time did the noise level at the Barcelona Avenue site perimeter exceed 10 dB(a) above the ambient noise level or 85 dB(a)
The SSHO performed total dust monitoring on a daily basis during the project at the site perimeter downwind of work location and at the site gate using a Miniram real time dust meter The summary of dust monitoring is presented in Table No 2 Total dust concentrations on site and off site did not exceed site criteria of 1 mgm3 and the action level of 05 nigny1
The summary of air monitoring for Volatile Organic Compounds (VOC) is presented in Table No 3 VOC concentrations in the working area did not exceed the on site criteria of 5 ppm in a breathing zone VOC concentrations on the site perimeter did not exceed real time off site criteria of 2 ppm
Five detail reports with results of air sampling were submitted during the project period
Sincerely Cashins amp Associates Inc
Evelina Vaughan Industrial Hygieflfst
CASHINS amp ASSOCIATES Inc
80 Mam Street bull Reading MA 01867 bull Phone61 7-944-4060 bull Fax 617-944-4082
07171996 1601 6179444082 CASHINS S ASSOCIATES PAGE 04
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89111995 1023 6172733(384 CASHINS ASSOCIATES PAGE 01
CASHINS amp Associates inc
Ifxtuitral Hygltne A fnvironmtnltt Tuning
W3SXLY HBALTH amp SAFETY PLAN COMPLIANCE SUMMARY R3PORT
CLIENT T foyd C o m a n
LOCATION gal era Acres Sx^perfund Site 8L-4 Area
DATES INCLUDED IN SUMMARY
toe
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SUMMARIZED BY FOR CASHINS amp ASSOCIATES INC
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CASHINSamp Associates Inc
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CLIENT T Fprd Company
LOCATION Salen Acres Suoerfund Site SL-4 Area
DATES INCLUDED IN SUMMARY
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CASHINS amp Associates Inc
Industrial Hygitnf amp CmimnmenUl Tinting
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Compan
LOCATION Salem Acres Superfund Site SL-4 Area
DATES INCLUDED IN SUMMARY
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LOCATION Salem Acrlaquoa Superfund Site 9L-4 Area
DATES INCLUDED IN SUMMARY
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CLIENT T Ford Company
LOCATION Salem Acres Superfund Site SL-4 Area
DATES INCLUDED IN SUMMARY J_
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PROJECT NAME_ SITE LOCATION
THE PURPOSE OF THE FOLLOWING STATEMENT IS TO DOCUMENT THE EXISTENCE OF A CONDITION OR CONCERN WHICH CASHINS amp ASSOCIATES INC BELIEVES WARRANTS IMMEDIATE CORRECTIVE ACTION POSSIBLE SOLUTIONS AND OR CORRECTIVE ACTIONS WILL BE INCLUDED IN THIS NOTIFICATION WHEN POSSIBLE THIS NOTIFICATION IS LIMITED TO SITUATIONS THAT REPRESENT EITHER IMMEDIATE DANGER TO LIFE OR HEALTH CONDITIONS OR PREVIOUSLY IDENTIFIED CHRONIC PROBLEMS THAT UNDERMINE OUR ABILITY TO EFFECTIVELY INSURE COMPLIANCE WITH THE REQUIREMENTS OF THE HEALTH AND SAFETY PLAN
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WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Company
LOCATION Salem Acres Superfund Site SL-4 Area
DATES INCLUDED IN SUMMARY T
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CLIENT T Ford Company T
LOCATION Salem AcrM Suoerfund Stta 8L-4 Araa
DATES INCLUDED IN SUMMARY
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07151996 18 fO 6179444082 CASHINS S ASSOCIATES PAGE 02
CASHINS amp Associates Inc
WBBKLY HEALTH amp SAFETY FLAK COMPLIANCE SUMMARY REPORT
CLIENT T Ford Compapv
LOCATION i Sal am Acrlaquolaquo Suparfund Sita SL-4 Area
DATES INCLUDED IN SUMMARY i bull pound7 mdash
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- barcode 14732
- barcodetext SEMS Doc ID 14732
![Page 4: SALEM ACRES SUPERFUND SITE SALEM, MA ...The truck loading pa d consisted of a crushed stone are sea t up along the east sid e o f SL-4 adjacent to the access road A. row of concrete](https://reader036.vdocuments.us/reader036/viewer/2022070114/60729b840fec4e6b4d136a16/html5/thumbnails/4.jpg)
Final Remedial Action Work Plan and submitted it to MEC on September 7 1995
The following summarizes milestones for the project
TASK BATES
Mobilization Septembers 1995
Site Preparation September 5 -8 1995
Excavation of Fly Ash September 8 - October 19 1995
Excavation of Contaminated October 18 - December 7 1995 Overburden and Fly AshSoil Mixtures
Bedrock Cleaning November 9 - December 5 1995
Placement of Random Fill November 16 - December 7 1995
Pumping amp Disposal of Ponded November 27 -30 1995 Water
Winter Shutdown December 8 1995 - May 2 1996
Placement of Loam Jute Mat May 2- 101996
Seeding May 14 1996
As-Built Survey May 21 1996
14 Project Photos
Photographs were taken during construction to document the work Representative photographs are included in this report Pre-construction photographs and a videotape were submitted prior to the start of work
2 REMEDIAL CONSTRUCTION ACTIVITIES
21 Mobilization and Site Preparation
TFCI mobilized the following equipment for this project
Cat 950 Front End Loader Komatsu PC 150 Excavator Komatsu PC 200 Excavator Cat D4H Dozer 1000 Gal Sedimentation Tank 9000 Gal Water Supply Tankers (2)
TFCI utilized the site office trailer set-up used by the contractor performing remediation of SL-5 Area (RUST E amp I) TFCI took over the rent and utility charges from DiBiase Realty Trust
The site preparation consisted of constructing a truck loading pad and a decontamination pad improving the access road installation of erosion controls and establishment of work zones
The truck loading pad consisted of a crushed stone area set up along the east side of SL-4 adjacent to the access road A row of concrete Jersey Barriers was set up along the west side of the truck loading pad to contain stockpiled ash and contaminated overburden from spilling on to the pad An excavator was used to load trucks The excavator was able to sit on the stockpiled material behind the Jersey Barriers to load trucks This enabled the operator to carefully load trucks and minimize dust The decontamination pad is discussed in Sec 23
The decontamination pad consisted of an HDPE-lined pad approximately 16 ft wide by 50 ft long The liner was filled with 34 inch crushed stone A sump was constructed to collect rinsate and pump it into a sedimentation tank Heavy timber planks were placed on top of the crushed stone to provide traction for truck tires and prevent rutting of the stone
For dust control TFCI set up a gas-powered high pressure pump capable of 75 gpm at 75 psi The pump fed the network of 2 inch and 1 2 inch flat fire hose with a nozzle for spraying down the work areas
The access road was improved by adding crushed stone as necessary and widening it on both ends of the truck loading and decontamination pads
Erosion controls consisted of silt fence and staked hay bales on the west side of SL-4 adjacent to WA-1 The location of the erosion controls was selected by GEI in conjunction with MADEP and USEPA
The following work zones were established for this site
Exclusion Zone (EZ) Contaminated Reduction Zone (CRZ) Support Zone (SZ)
The limits of these zones were established to conform with the site geometry operational requirements and Health and Safety requirements Initially the EZ was the area within the perimeter boundary of SL-4 except it extended west to the location of the erosion controls The limits of the EZ did not change until all contaminated soil and debris was removed and verified by confirmatory sampling
and testing
The CRZ was established at the top of the slope along the east side of SL-4 The decontamination pad was a major part of the CRZ All worker and equipment decontamination was performed in the CRZ A bootglove washing station was set up in the CRZ along with PPE disposal containers and a handwash PPE was disposed of at Turnkey Landfill in Rochester NH
The Support Zone was established on the east side of the access road opposite SL-4 The office trailer sanitary facilities and water supply were set up in the Support Zone A 2-inch water supply line was temporarily installed under the access road to supply water for decontamination equipment in the CRZ from the water tankers in the SZ
TFCI also initiated a security program to provide full time security watch on site During non-work hours including weekends a security guard was posted in the site trailer The security guard made hourly rounds of the support zone and Access Road including the Barcelona Avenue gate Logs were maintained of security shifts
22 Clearing
Clearing was performed incrementally during the project Trees were cut by chain saw and stockpiled in the Support Zone along the access road Once the majority of trees were cut and stockpiled they were loaded onto 100 cy trailers for off-site disposal Disposal consisted of chipping and burning at a facility in Maine Hauling and disposal was done by Wood Waste of Boston Inc
Phragmites were mixed in with the fly ash during excavation The phragmites constituted a very small portion of the volume of fly ash
23 Decontamination Dust Control and Health and Safety Monitoring
As mentioned above truck loading and decontamination pads were constructed along the east side of the site adjacent to the access road TFCI used a hydraulic excavator to load dump trailers from stockpiles By using an excavator we were able to minimize spillage of material onto the outside of the trailers However all trucks were considered potentially contaminated and were decontaminated by washing down over the decontamination pad
TFCI constructed an overhead spray bar set-up which trucks drove under after loading The wheels and sides of the trucks were then washed down with hoses The decontamination water rinsate was collected in the sump of the HDPE-lined decontamination pad Rinsate was pumped into a 1000 gallon sedimentation tank After removal of the fines the decontamination water was used for dust control
The fly ash was found to be quite dry particularly in the upper 10 to 15 ft and prone to dusting easily TFCI used imported water to keep the fly ash moist in stockpiles and after loading a truck A total of 180000 gallons of water was imported to the site for decontamination and dust control The majority of this water was used for dust control on fly ash The dust control measures employed were quite successful No dust levels were measured exceeding the site criteria at the Barcelona Avenue gate or in the work zones
For Health and Safety Monitoring TFCI contracted with Cashins amp Associates (CA) CA prepared a Health and Safety Plan and performed on-site monitoring of air and noise in the work zone and at the site perimeter A Health and Safety Phase-Out Report prepared by CA is contained in Appendix C
24 Excavation and Loading of Fly Ash
TFCI used two methods for excavating the fly ash and moving it to a stockpile Due to the steep slopes tight quarters and poor traction on the fly ash it was impossible to use a front end loader at the SL-4 site Initially we used an excavator and a bulldozer to excavate and move fly ash to stockpiles
As the mounded area of the fly ash was removed and the excavation began to consist of a steeply sloped face of fly ash we used two excavators The excavators worked as a bucket brigade to excavate and move material up the slope to the stockpile area Material was handled several times to reach the stockpile As the bottom of fly ash level was approached the excavators were able to excavate the fly ash close to the interface between fly ash and contaminated overburden and soilfly ash mixtures
All loading of fly ash was done by an excavator with a large bucket (2 cy capacity) Table 1 summarizes the daily quantities of fly ash loaded In general approximately the same quantity of fly ash was excavated as was loaded each day No significant stockpiles were maintained during the work A stockpile of fly ash excavated on SLshy5 area (by others) was loaded on the first full day of hauling of fly ash from SL-4
25 Excavation and Loading of Contaminated Overburden and SoilFly Ash Mixture
Excavation of contaminated overburden soilfly ash mixture and debris (referred to hereafter as contaminated overburden) was performed using excavators similar to the procedures for fly ash The horizontal limits of excavation were determined by GEI Consultants Inc and are described in the Demonstration of Compliance report prepared by GEI In general the horizontal limits are as follows
Northern - Defined by DA-1 Area Eastern - Defined by confirmatory sampling and analysis along
the Access Road Southern - Defined by SL-5 Area except for Area 1 which was
incorporated into SL-4 site remediation work Western - Defined by WA-1 Area
The bottom of excavation was sampled for confirmatory analysis by GEL The results of this analysis are described in the Demonstration of Compliance Report
Table 2 summarizes the daily quantities of contaminated overburden loaded Approximately the same daily quantity was excavated No significant stockpiles of contaminated overburden were maintained
Where bedrock was encountered contaminated soils were scraped off with the excavator The remaining material was removed as part of bedrock cleaning (see Sec 27) A number of boulders were encountered in the overburden MEC elected to have TFCI decontaminate the boulders on the decontamination pad and then incorporated them into the random fill
26 Ponded Water
Removal of fly ash and contaminated overburden along the western side of SL-4 resulted in a low area which collected both surface water run-off and groundwater seepage This area became a temporary pond containing approximately 100000 to 150000 gallons of water The level fluctuated with the level of the adjoining wetlands
In order to discharge the ponded water to the wetlands (WA-1) the discharge would have to meet Federal drinking water quality standards TFCI arranged for sampling and testing of the ponded water The results are contained in Appendix A Although the water met requirements of USEPA and MADEP for chemical contaminants the water was quite turbid and no practical means of removing suspended solids was available
A request was made to SESD to dispose of the ponded water at its Salem Treatment Facility SESD approved this request on November 20 1995
The ponded water was pumped into conventional septage hauling vehicles on November 27 through 30 1995 A total of 125000 gallons was transported to SESD for disposal Random fill was placed in the low area immediately following pumping of ponded water to avoid collection of additional water
27 Bedrock Cleaning
As required by the Specifications all exposed bedrock was cleaned of all fly ash and
contaminated overburden Several techniques andor methods were used to clean bedrock including
a) Manual broom and shovel work b) Compressor with air gun to loosen material from crevices with water
used for dust control c) A Vac-All truck using water andor compressed air to loosen
material d) A broom attached to the bucket of an excavator
The surface of exposed bedrock was generally quite irregular and required considerable effort to remove soil and fly ash from cracks and crevices In some areas the rock is highly weathered and can be removed In these areas a determination was made in conjunction with GEI as to when to stop removal of weathered bedrock
During placement of random fill and loam some areas of exposed bedrock became re-covered with these earth materials TFCI proposed to topsoil and seed on these areas rather than re-cleaning the bedrock GEI EPA and MEC accepted this proposal
3 SITE RESTORATION
31 Random Fill
Random fill for the site restoration was obtained from a borrow pit located on Munson Street in Peabody MA GEI conducted confirmatory sampling of the borrow source The results are contained in the Demonstration of Compliance Report A grain size analysis is provided in Figure 1 A total of 1176 cy of random fill was delivered to the site and spread over all exposed soil subgrade areas The thickness is 6 inches except along the west side of the site where it ranges up to 5 ft thick where contaminated soil and fly ash were encountered at a deeper level (See Sec 4)
The random fill was spread and compacted using a CAT D4H dozer
32 Loam and Seeding
In the Spring of 1996 after Winter shutdown TFCI placed and spread a 6-inch layer of loam The loam was obtained from a loam stockpile located at a new residential subdivision in Ayer MA called Bennetts Brook and furnished to the site by D amp H Loam Company A total of 695 cy of loam was delivered to the site GEI conducted confirmatory sampling of the loam source The results are contained in the Demonstration of Compliance Report A topsoil analysis report is provided as
Figure 2
The loam was spread using a CAT D4H dozer Areas of the slope where the grade was steeper than 4HIV were first hand-seeded and then covered with Erosion Control and Revegetation Mat (ECRM) The entire loamed area was then hydro-seeded on May 14 1996 The seed used is Massachusetts Highway Department Specification M6030 Slope and Shoulder Mix
33 FencingDemobilization
In order to remove fly ash andor contaminated overburden which extended onto DA-1 it was necessary to remove the fence along the south side of DA-1 After completion of remediation work the fence was replaced Because of the winter shutdown TFCI reinstalled the fence prior to site restoration work to secure the DAshy1 area
Following placement of the random fill TFCI demobilized for winter shutdown Due to an early snowfall it was impossible to loam and seed the site prior to winter shutdown TFCI demobilized equipment and support facilities December 8-13 1995
In the Spring of 1996 it was only necessary to mobilize a dozer and small excavator to place and spread loam
4 QUANTITY SURVEYS AND AS-BUILT PLANS
41 Fly Ash Quantity Survey
In order to calculate the insitu quantity of fly ash for payment TFCI engaged a subcontractor T F Moran for survey work and quantity estimates T F Moran performed an existing conditions topographic survey on April 21 1994 for design studies conducted by GEI Consultants Inc This survey was updated and verified on September 8 1995 by T F Moran for TFCI In addition a stockpile of fly ash removed from SL-5 was also surveyed on this date
T F Moran surveyed the bottom of fly ash on October 18 1995 The results of the fly ash quantity surveys are shown on Figure 3 The quantities of fly ash are as follows
SL-4 Fly Ash 12750 cy SL-5 Fly Ash (stockpiled on SL-4) 520 cv
13270 cy
In addition there was an estimated 1500 cy of fly ash not included in the TF
Moran surveys because the material was in or under active stockpiles at the time of the survey The quantity survey and method of calculation is described in a letter from T F Moran dated January 15 1996 and contained in Appendix B
42 Limits of Remediation
In order to document the limits of remediation T F Moran surveyed the site on November 1 and December 5 1995 Areas where contaminated overburden were removed were surveyed at these times including the limits of exposed bedrock The results of these surveys are shown on Figure 4 The limits of SL-4 site remediation are as follows
Total Site Area Remediated 50860 sf Exposed Ledge 19990 sf
Site Restoration Area 30870 sf
In addition Area 1 is approximately 5416 sf
Note that the total quantity of contaminated overburden and fly ashsoildebris mixture was 6056 tons compared to the estimated 4100 tons from the design studies The primary reasons for the increase include the following
Incorporation of Area 1 from SL-5 in the SL-4 site remediation work
The northern limit of excavation extended further into DA-1 than anticipated in the RA Work Plan
Excavating further west into WA-1 than anticipated in the RA Work Plan
VOC contaminated fly ash and soil in the northwest corner near DAshy1 at a considerable thicknessdepth
The limits of remediation survey are described in the T F Moran letter contained in Appendix B
43 Final As-Built
A final as-built survey was performed by T F Moran on May 21 1996 The results of the survey are shown on Figure 5
TABLE 1 SUMMARY OF ASH REMOVAL
SALEM ACRES SUPERFUND SITE SL-4 AREA
DATE NOMBEraquo0poundLOADS
0AILY TOTAL ifrotfS) i
SEPTS 1 1750
SEPT 1 1 8 13470
SEPT 12 10 21080
SEPT 13 20 45800
SEPT 14 23 50100
SEPT 15 20 43160
SEPT 18 23 46870
SEPT 19 24 54780
SEPT 20 26 52800
SEPT 21 25 47700
SEPT 22 25 46915
SEPT 25 26 51950
SEPT 26 29 56820
SEPT 27 30 55660
SEPT 28 30 58410
SEPT 29 26 53520
OCT2 26 54600
OCT3 26 57000
OCT4 19 41080
OCT5 22 49240
OCT6 26 61860
OCT 10 18 47180
OCT 11 12 33860
OCT 13 17 439 40
OCT 17 3 7600
OCT 19 3 7720
CtnVfOtATIVE TOTAL (TONS)
1750
15220
36300
82100
132200
175360
222230
277010
329810
3775 10
424425
476375
5331 95
5888 55
647265
700785
755385
812385
853465
902705
9645 65
1011745
1045605
1089545
1097145
1104865
TABLE 2 SUMMARY OF CONTAMINATED
OVERBURDEN REMOVAL SALEM ACRES SUPERFUND SITE SL-4 AREA
DATE
on 19 OCT 20
OCT 23
OCT 24
OCT 25
OCT 26
OCT 27
OCT 31
NOV 1
NOV2
NOV 6
NOV 8
NOV 9
NOV 21
NOV 28
DEC 7
NUMBER OF LOADS
14
14
14
13
14
16
18
18
12
4
4
8
8
8
9
2
DAILY TOTAL (TONS)
46121
41649
49314
448 59
46225
48054
62358
56186
491 56
14209
14025
29010
27604
35513
33447
7885
CUMULATIVE TOTAL (TONS)
46121
87770
137084
181943
228168
276222
338580
394766
443922
458131
472156
501166
528770
564283
597730
6056 1 5
- -
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Oct 17 1995 823PM P02 From LTTS OF Mfl INC PHONE No 617 438 S21S
GRftIN SIZE DISTRIBUTION TEST REPORT C c c e
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bull bull a 96 3 4 777
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075 90 40 505 bullSILTY CLAYEY GflNO 0 375 34 50 44 4
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3X1 GRAIN SIZE 200 257
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xC COEFh 1C1CNT5 UTS OF MASSACHUSETTS INC bull
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GtoneHam Mft 03 IBB Date 101195 Gamn 1 c- No 44fi1A
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From UTS OF Mfl INC PHONE No 517 438 6216 Oct 17 1995 824PM F03
SOT ANALYSIS REPORT FOR NEW LAWN 101195
SOIL AND PLANT TISSUE TESTING LABWEST EXPERIMENT STATIONUNIVERSITY OF MASBACIIUfiFTTr AMHERST MA 01003
LAB NUMBER 3951010-107 BAG NUMBER 23467
DATE BFNT f
SOIL FROM COUNTY SOIL WEIGHT 537 g5cn CROP TURFORASS
UTS OF MASS INC COMMENTS ORGANIC MATTER 6 RICHARDSON LANE STONEHAM MA 02180
SAMPLE ID 4461B
LIMESTONE AND FERTILIZER RECOMMCNDATIONS FOR NEW LAWN CONSTRUCTION
No limestone ia required If peat mooc or similar material ia to be incorporated) see enclosed fact sheet
Fertilizer (per 10OO sq ft) 2 1ba N 2 Ibo P2O5 and O 1 bs KZO
Many fertilizer sources and rates may combine to provide acceptable turfgraes establ iahmont either from seed or aod One or two options baaed on this soil teat follow
Incorporate EITHER a 17-23-6 starter fert111zar at 10 lbs1000 sq ft OR a 30-3-3 lawn fertilizer at 7 1b81000 aq ft plus a 0-45-0 (triple superphosphate) fertilizer at 4 lbs1000 aq ft Hnto the top 3 to 4 inches of soil Retest Bull ona year after turf establishment
PLEASE read the enclosed fact sheets for niora specific Information on fertilization and liming procadurea
SOIL pH 71 NITROGEN NO3-N = Oa ppm NH4-N = 5 ppm BUFFER pH 74 ORGANIC MATTER 72 X (Desirable range 4-10X)
NUTRIENT_LEVELS_PPM_| Low Medium High Very High Phosphorus (P) 8 |XXXXXXXXXXXXX Potaaaium (K) 292 [XXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXX Calcium (Ca) 237S XXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXX Magnesium (Mg) 237 JXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXX
CATION EXCII CAP PERCENT BASE SATURATION MICRONUTRIENT LEVELS 130 Meq100g K= 52 Mg=134 Ca=816 ALL NORMAL
CXTRACTABLE ALUMINUM 41 ppm (Soil ranglaquo 10-250 ppm)
The lead level in thio soil 1s low
COMPUTER PROGRAM5-RECOMMENDATIONRbYOtHIOFPtANT~ampSOILSCI UMASS-AMHERST
Figure 2
TARGET SHEET
THE MATERIAL DESCRIBED BELOW WAS NOT SCANNED BECAUSE
(X) OVERSIZED
() NON-PAPER MEDIA
() OTHER
DESCRIPTION DOC 14732 DRAFT FINAL REMEDIAL CONSTRUCTION REPORT FIGURE 3 TOPOGRAPHIC PLAN SL-4 AREA BOTTOM OF FLY ASH SALEM ACRES SHEET 1 OF 1
THE OMITTED MATERIAL IS AVAILABLE FOR REVIEW BY APPOINTMENT
AT THE EPA NEW ENGLAND SUPERFUND RECORDS CENTER BOSTON MA
TARGET SHEET
THE MATERIAL DESCRIBED BELOW WAS NOT SCANNED BECAUSE
(X) OVERSIZED
() NON-PAPER MEDIA
() OTHER
DESCRIPTION DOC 14732 DRAFT FINAL REMEDIAL CONSTRUCTION REPORT FIGURE 4 TOPOGRAPHIC PLAN SL-4 AREA LIMIT OF REMEDIATION SALEM ACRES SHEET 1OF1
THE OMITTED MATERIAL IS AVAILABLE FOR REVIEW BY APPOINTMENT
AT THE EPA NEW ENGLAND SUPERFUND RECORDS CENTER BOSTON MA
TARGET SHEET
THE MATERIAL DESCRIBED BELOW WAS NOT SCANNED BECAUSE
(X) OVERSIZED
() NON-PAPER MEDIA
() OTHER
DESCRIPTION DOC 14732 DRAFT FINAL REMEDIAL CONSTRUCTION REPORT FIGURE 5 TOPOGRAPHIC PLAN SL-4 AREA AS-BUILT PLAN SALEM ACRES SHEET 1 OF 1
THE OMITTED MATERIAL IS AVAILABLE FOR REVIEW BY APPOINTMENT
AT THE EPA NEW ENGLAND SUPERFUND RECORDS CENTER BOSTON MA
(i)
^mft^m
VIEW OF BARCELONA AVENUE THROUGH ENTRANCE GATE PRECONT RUCTION
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(2)
VIEW OF ACCESS ROAD LOOKING NORTH SL-4 ON LEFT PRECONSTRUCTION
VIEW OF ACCESS ROAD LOOKING NORTH SL-4 ON LEFT DA-1 TO LEFT OF PICKUP TRUCK
PRECONSTRUCTION
(3)
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
O ID a CO z O OHI
CO UJ
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(5)
VIEW OF BOUNDARY BETWEEN SL-4 AND DA-1 LOOKING WEST PRECONSTRUCTION
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(6)
EROSION CONTROLS LOOKING NORTH FROM CORNER OF SL-4SL-5 ADJACENT TO WA-1 PRECONSTRUCTION
(7)
TRUCK LOADING PAD LOOKING NORTHWEST FROM SUPPORT ZONE
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(8)
DECONTAMINATION PAD LOOKING NORTHWEST FROM SUPPORT ZONE
(9)
EXCAVATION OF FLY ASH LOOKING NORTHWEST FROM CRZ NOTE WATER FOR DUST CONTROL
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(10)
VIEW LOOKING WEST AFTER REMOVAL OF FLY ASH NOTE WA-1 BEYOND EROSION CONTROLS
(11)
EXCAVATION OF CONTAMINATED OVERBURDEN LOOKING SOUTH FROM DA-1 BOUNDARY
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(12)
VIEW OF RESTORED SITE LOOKING WEST TOWARD WA-1
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VIEW OF RESTORED SITE LOOKING NORTH TOWARD DA-1 ALONG ACCESS ROAD
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(15)
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ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(18)
VIEW OF RESTORED SITE ON DA-1 SIDE OF FENCE - LOOKING WEST SL-4 ON RIGHT
APPENDIX A
ANALYTICAL RESULTS FOR
PONDED WATER
110795 1638 copy617 890 3883 TMA-WALTHAM ] 002007
PRELIMINARY REPORT UNAUDITED RESULTS
Thenno Analytical 300 Second Avenue PO Box 521 Waltham HA 02254
Attn Client Services Phone (617) 890-7200
Cashins amp Associates Order S5-11-034 55 Cambridge Street Date 110795 1522 Burlington HA 01803 Work ID Salem Acres Water
Date Received 110295 Attn Bob Cashins Date Completed
Purchase Order NA Invoice Number Client Code CASHINS
SAMPLE IDENTIFICATION
Sample Sample Number Description 01 11019S-924-01A
Sample Number 04
Sample Description
110195-9Z4-01D 02 110195-924-01B 05 110195-924-01E 03 110195-924-01C
Certified By
110795 1638 copy617 890 3883 TMA-WALTHAM 003007
PRELIMINARY REPORT UNAUDITED RESULTS
Order f S5-11-034 Thermo Analytical Page 2 110795 1522 TEST RESULTS BY SAHPLE
Test Description Volatile Organics- Aqueous Method EPA_8240 Test Code Collected 110195 02-00 Category WATER
DATE INJECTED 110695 DILUTION FACTOR 100 All results reported 1n ugL
COMPOUND RESULT DET LIMIT COMPOUND RESULT
Chloromethane U 10 Broroodi chl oromethane U Vinyl Chloride U 10 2-Chloroethyl Vinyl Ether U
Bromxnethane U 10 4-dethyl -2-pentanone U Chloroethane U 10 c1 3-1 3-Di chl oropropene U
Trichlorofluoronwthane U 50 Tol uene U Acetone 17 10 trans-1 3-Di chl oropropene LI
11-Oichloroethene U 50 11 2-Tri chl oroethane J Carbon Dlsulfide U 50 2-Hexanone U
Methyl ene Chloride U 50 Tetrachl oroethene U 12-Oichloroethene (total) U 50 D1 bromochl oromethane U
11-01 Chloroethane U 50 Chlorobenzene U Vinyl Acetate U 10 Ethyl benzene U
2-Butanone U 10 in and p-Xylene U Chloroform U 50 o-Xylene U
111-Tri Chloroethane U 50 Styrene U Carbon Tetrachlortde U 50 Broraoform U
Benzene U 50 112 2-Tat rachl oroethane U 12-01 Chloroethane U 50 1 3-01 chl orobenzene U
Trichloroethene U 50 I 4-Di chl orobenzene U 12-Dichloropropane U 50 12-01 chl orobenzene U
SURROGATE STANDARDS RESULT LEVEL X RECOVERY
12-Dichloroethane-D4 52 50 104 Toluene-08 47 50 94
l-Bromo-4-fluorobenzene 56 50 112
NOTES AND DEFINITIONS FOR THIS REPORT U =bull Undetected at stated detection limit
VOAJI
OET LIMIT
50 50
10 50 50 50 50 10
5 0 50 5 0 5 0 50 50 50 50 50 50 50 50
110795 1639 copy617 890 3883 TMA-WALTHAM copy004007
PRELIMINARY REPORT UNAUDITED RESULTS
Order t S5-11-034 Thermo Analytical Page 4 110795 1522 TEST RESULTS BY SAMPLE
ianple Description 110195-924-010 Lab No 04A Test Description RCRA Metals 1n Water Method SW846 Test Code
Collected 110195 0200 Category WATER
METAL RESULT DETECTION LIMIT METAL RESULT DETECTION LIMIT
Ag Silver U 10 As Arsenic 870 50
Ba Bar inn B69 10 Pb Lead U 50
Cd Cadmium U 50 Se Sel en1 um Z15 50
Cr Chromi um U 20 Hg Mercury U 020
NOTES AND DEFINITIONS FOR THIS REPORT All results reported in ugL U gt Undetected at stated detection limit
110795 1640 Q617 890 3883 TMA-WALTHAM 0005007
PRELIMINARY REPORT UNAUDITED RESULTS
Order S5-11-034 Thermo Analytical Page 5 110795 1522 REGULAR TEST RESULTS BY TEST
Chemical Oxygen Demand Mlnimun Maximum Method EPA600 4101
Sap Sample Description Result Units Limit Prepared Analyzed By 05A 110195-924-01E 64 bullgL 50 110395 110395 JD
Petroleum Hydrocarbons-H20 Minimum Maximum Method EPA600 4181
Samp Sample Description Result Units Limit Prepared Analyzed By 01A 110195-924-01A 108 mgL 050 110395 110395 JO
110795 1640 reg617 890 3883 TMA-WALTHAM copy006007
PRELIMINARY REPORT UNAUDITED RESULTS
Order I S5-11-034 Therm Analytical Page 6 110795 1522 TEST METHODOLOGIES
USEPA Test Methods for Evaluating Solid Wastes (SUS46 Third Edition) Method 7470 - Preparation of water for Mercury analysis
USEPA Test Methods for Evaluating Solid Vastes (SW846 Third Edition) Method 3010 - Add digestion of aqueous samples and extracts for total metals for analysis by Flame Atomic Absorption Spectroscopy or Inductively Coupled Plasma Spectroscopy
USEPA Test Methods for Evaluating Solid Vastes (SWB46 Third Edition Method 8270 mdash Gas ChroroatographyMass Spectrometry for PAHs
Volatile Organics in Water - Hazardous Substance List
SV846 Method 8240 - Modified
Test Methods for Evaluating Solid Waste SU-846 US EPA Office of Solid Waste and Emergency Response Washington 3rd Edition
Aqueous sanples are analyzed in accordance with Method 8240 using a purge and trap technique followed by 64s ChromatographyMass Spectroscopy
Quality assurance procedures for GCMS Include daily tuning and calibration of the mass spectrometer and the use of surrogate standards in each sample to monitor method performance Quantitatton is performed by the Internal standard method Analysis of blanks duplicate samples and standards are run frequently as further quality assurance procedures
USEPA Test Methods for Evaluating Solid Wastes (SW846 Third Edition) Method 3S10 mdash Separatory Funnel Liquid-Liquid Extraction
EPA-6004-79-020 - Chemical Oxygen Demand - Titrimetric Mid-Level Method 4101
EPA6004-79-020 - Petroleum Hydrocarbons 1n Water Total Recoverable Method 4181 (Spectrophotometric Infrared)
110795 1641 copy617 890 3883 TMA-WALTHAM copy007007
APPENDIX B
QUANTITY SURVEY DOCUMENTATION
TFMORAN INC Surveying - Engineering - Land Planning SoilsWetlands Mapping - Landscape Architecture
January 15 1996
Mr Jack Enos Vice President TFord Company Inc 118 Tenney Street Georgetown MA 01833
RE Survey Results - Salem Acres - SL4 Area Salem Massachusetts
Dear Jack
This letter amends the letter of December 13 1995 per our review last week
TFMoran Inc performed topographic surveys at the Salem Acres site on April 21 1994 for GEI Consultants prior to removal of material and for TFord Company on October 18 1995 after the removal of material The survey data from the original survey in 1994 was adjusted thirty feet higher to correct for a datum difference from current site datum This was due to the original reporting of the Site Benchmark (TP34) elevation as 11464 rather than 14464 which is the correct elevation
Once both topographic surfaces were on the site datum the raw cut volume was obtained by Eaglepoint (Volumes Module) Software utilizing the prismoidal method comparing the two surfaces For reference please see the attached topographic plan which superimposes the October 15 1995 contours (dark lines) over the April 21 1994 contours The volume is based on the intersection of the two surfaces Also it was noted that stock piles of material did exist on site which were not surveyed at the time
The final raw cut volume arrived at by the above methods is 12749 Cubic Yards
In November and December of 1995 the site was resurveyed to locate the area of exposed ledge at the site The results of this survey are shown on the attached topographic worksheet dated November 3 1995 and last revised January 15 1996 The results of the survey indicate the total site area to be 50860 sq ft or 117 acres The total area of exposed ledge surveyed is 19990 sq ft or 46 acres If you have any questions regarding the above call me directly Thank you
Sincerely
John W Myhaver Jr ^_ Field Operations Manager
Enclosure ItorLltr
Route 101 Bedford NH 03110 Phone (603) 472-4488 FAX (603) 472-9747
APPENDIX C
HEALTH AND SAFETY PHASE-OUT REPORT
HEALTH AND SAFETY PHASE-OUT REPORT SALEM ACRES SL-4 AREA
Introduction
During remediation work on SL-4 Health and Safety Monitoring was performed Cashins amp Associates Inc of Reading MA performed the following work as a subcontractor to TFCI
1) Preparation of a site-specific Health and Safety Plan (dated September 1 1995)
2) Provide a Field TechnicianIndustrial Hygienist to serve as Site Safety and Health Officer (SSHO) and to conduct air and noise monitoring
3) Provide a Certified Industrial Hygienist to review Health and Safety and to conduct site specific training (record of training included at end of Appendix C)
4) Collect 8-hour air samples for worker exposure and ambient air at the Barcelona Avenue gate Arrange for analysis of the samples and report results
5) Prepare daily and weekly Health and Safety reports
6) Prepare a Health and Safety Phase-Out Report
In general the following health and safety practices were followed
1) All workers wore hard hats safety glasses work boots gloves and hearing protection as minimum level PPE
2) When working in the exclusion zone workers wore in addition to above tyvek rubber overboots and rubber coated gloves When dust was a potential concern an industrial grade dustmist mask was also worn This level of PPE was considered Level D modified
3) Workers leaving the exclusion zone removed PPE (tyveks gloves boots and masks) in the support zone and either disposed of the items or decontaminated them
4) Workers andor visitors without 40-hour OSHA training were not permitted to enter the exclusion zone
Attached is a report prepared by Cashins amp Associates along with weekly Health and Safety Summary Reports prepared by the Field Hygienist In summary the air monitoring results indicate no levels exceeding the applicable exposure guidelines except one instance
During excavation of contaminated overburden in the northwest comer of the site an area of VOC contaminated soil was encountered Total VOCs levels measured using a PID exceeded the action level established in the Health and Safety Plan The SSHO advised TFCI to upgrade to Level C PPE in order to backfill the excavation in this area TFCI equipment operator upgraded and backfilled the area The SSHO in consultation with the Cashins CIH advised TFCI to avoid work in this area until the contaminants were characterized GEI sampled the material for waste characterization analysis and provided the results to TFCI Based on the results an action level was established by the CIH for the specific contaminants found Further PID measurements indicated levels below the new action level and work was resumed
The noise monitoring indicated that the noise level at the Barcelona Avenue gate was not exceeded Only one instance of excess noise level in the work zone was recorded (10 db(a) above the ambient noise level or 85 db(a)) Workers wore hearing protection in this instance
mdash 07171996 1601 6179444032 CASHIMS S ASSOCIATES PAGE 02
CASHINS amp Associates Inc
ItxhalrM Hy-gifnr A Invtronmtnltl Tttling
July 17 1996
Mr Jack Enos T Ford Company Inc USTenney Street Georgetown MA 01833
Dear Jack
The Site Safety and Health Officer (SSHO) from Cashing amp Associates Inc performed daily inspections of the SL-4 area Salem Acres Superfund Site between 9595 and 12195 in accordance with the Health amp Safety Plan (HSP) for the site Daily inspection logs were submitted every day No accidentsincidents were reported during the work period
In accordance with the Health amp Safety Plan the SSHO performed daily air and noise monitoring at the site during Ac project Samples were collected for metals (lead beryllium chromium arsenic) and Polynuclear Aromatic Hydrocarbons (PAHs) at the site perimeter and for workers exposure determination Coal Tar Pitch Volatiles (a benzene soluble extractables) were also used to determine the workers exposure to PAH compounds Coal Tar Pitch Volatiles (CTPV) were analyzed using OSHA 58 Method If CTPV levels oq personal samples exceed the site criteria of 02 ragm3 the sample was submitted for PAHs analysis All air samples on the site perimeter were analyzed for PAH compounds
Site monitoring air sample collection and results report were done under the supervision of a Certified Industrial Hygienist
Full shift personal worker exposure samples were collected once a week Ambient air samples were collected at the Barcelona Avenue gate about 20 feet to the west of the site gate to determine if site contaminants were migrating off site The ambient air samples were also collected once a week during the project except on rainy days and days without work with contaminated soil
All air samples were analyzed by the American Industrial Hygiene Association accredited ESA Laboratories Inc using the following methods PAHs - NIOSH 5515 Lead - NIOSH 7082 Beryllium - NIOSH 7102 Chromium - NIOSH 7024 Arsenic - NIOSH 7900 Coal Tar Pitch Volatiles - OSHA 58 All methods used are accepted by the industrial hygiene community for 8-hour exposure assessment EPA methods are usually used for ambient air measurements
CRErORTTFOmiOO
80 Mam Street bull Reading MA 01867 bull Phone- 61 7-944-4060 bull Fax 61 7-944-4082
07171996 1601 6179444032 CASHIMS amp ASSOCIATES PAGE 03
The results of air samples for metals and PAHs are presented in Table No 1
All concentrations of metals and PAHs at the site perimeter (Barcelona Avenue) and active work zones were below the OSHA Permissible Exposure Limits (PEL) and the American Conference of Governmental Industrial Hygicnists Threshold Limit Value (ACGIH TLV) Two personal samples collected on October 19 and October 23rd showed Coal Tar Pitch Volatiles (CTPV) results above OSHA PEL and AIHA TLV limits Both samples were resubmittcd to the lab for further analysis to determine if PAH compounds are present because the CTPV results were above site criteria
The results of the PAH concentrations for the personal sample on Mark Goodwin on October 19 1995 during excavation and washing trucks and for the personal sample on Ron Maker on October 23 1995 during excavating and cleaning rocks by compressed air were below OSHA PEL and ACGIH TLV limits
The SSHO performed noise monitoring according to the HSP at the exclusion zone and at the Barcelona Avenue site perimeter fence A Dupont sound level meter was used for noise monitoring The noise level in the exclusion zone during all operations except one did not exceed the on site criteria of 85 dB(a) During a short time when the air compressor had been used to clean rocks the sound level in the exclusion zone next to the air compressor did exceed 85 dB(a) Ear protection devices were worn by the workers during that operation At no time did the noise level at the Barcelona Avenue site perimeter exceed 10 dB(a) above the ambient noise level or 85 dB(a)
The SSHO performed total dust monitoring on a daily basis during the project at the site perimeter downwind of work location and at the site gate using a Miniram real time dust meter The summary of dust monitoring is presented in Table No 2 Total dust concentrations on site and off site did not exceed site criteria of 1 mgm3 and the action level of 05 nigny1
The summary of air monitoring for Volatile Organic Compounds (VOC) is presented in Table No 3 VOC concentrations in the working area did not exceed the on site criteria of 5 ppm in a breathing zone VOC concentrations on the site perimeter did not exceed real time off site criteria of 2 ppm
Five detail reports with results of air sampling were submitted during the project period
Sincerely Cashins amp Associates Inc
Evelina Vaughan Industrial Hygieflfst
CASHINS amp ASSOCIATES Inc
80 Mam Street bull Reading MA 01867 bull Phone61 7-944-4060 bull Fax 617-944-4082
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40 SALEM ST bull LYNNFIELD MA 011J40 bull TEL 617-2-)5-J77J - FAX ()l7-MS-tUrj
OSHINSamp Associates Inc
Industrill Hygiene amp Environnivnljl fating
SITE SPECIFIC amp HAZARD COMMUNICATIONS TRAINING SIGN-IN SHEET
DATE poundLOCATION OF TRAINING
TIME
NAME COMPANY SIGNATURE
j
40 SAUM ST bull LYNNFIELD MA (J1J40 bull TEL 617-2-T 1773 FAX (gtI7 M5-iU7i
CASHINS amp Associates Inc
Industrie Hygitmt amp tnvironmvnlal
SITE SPECIFIC amp HAZARD COMMUNICATIONS TRAINING SIGN-IN SHEET
DATE
LOCATION OF TRAINING
ir bull vr~ TIME - laquo t bullgt
NAME COMPANY SIGNATURE
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40 SALEM ST bull LYNNFIELD MA 01J40 bull TEL 617-245-J77J bull FAX (gtl7--IS4()rj
89111995 1023 6172733(384 CASHINS ASSOCIATES PAGE 01
CASHINS amp Associates inc
Ifxtuitral Hygltne A fnvironmtnltt Tuning
W3SXLY HBALTH amp SAFETY PLAN COMPLIANCE SUMMARY R3PORT
CLIENT T foyd C o m a n
LOCATION gal era Acres Sx^perfund Site 8L-4 Area
DATES INCLUDED IN SUMMARY
toe
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SUMMARIZED BY FOR CASHINS amp ASSOCIATES INC
55 CAMBRIDGE STREET bull SUITE 201 bull BURLINGTON MA 01803 laquo TEL 61 -273-9080 bull FAX 67-273-9C84
09111995 1023 6172739084 CASHINS ASSOCIATES PAGE 01
CASHINSamp Associates Inc
Induttrml Hygttnr t Emtroomtnttl Ttstinf
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Fprd Company
LOCATION Salen Acres Suoerfund Site SL-4 Area
DATES INCLUDED IN SUMMARY
000 mdash0
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SUMMARIZED BY FOR CASHINS 4 ASSOCIATES INC
55 CAMBRIDGE STREET bull SUITE 201 bull BURLINGTON MA 01803 raquo- TEL 6J 7-273-9080 bull FAX 617-273-9084
CASHINS amp Associates Inc
Industrial Hygitnf amp CmimnmenUl Tinting
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Compan
LOCATION Salem Acres Superfund Site SL-4 Area
DATES INCLUDED IN SUMMARY
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CASHING X ASSOCIATES PAGE
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CASHINSamp Associates Inc
WEEKLY HEALTH amp SAFBTT PLAN COMPLIANCE SUMMARY REPORT
CLIENT ^T Ford Combanv
LOCATION Salam Aerag SL-4
DATES INCLUDED IN SUMMARY
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SUMMARIZED BY FOR CASHINS amp ASSOCIATES INC
55 CAMBRIDGE STREET bull SUITE 201 bull SURUNCTON vu 01803 TEL 61 rori-^oao FAX 61 ~ rj
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55 CAM8RJDCpound STWET bull SUTTE201 eolaquolNCTONMAOJlaquo03 TIL 6t7shy
07161996 1650 6179444082 CASH INS amp ASSOCIATES PAGE 08
CASHINSamp Associates Inc
Intutttitl Myffcnt t InvtmnmmUt Itnl
WEEKLY HEALTH 6 SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Fortjl Cqjapany
LOCATION Salem Acrlaquoa Superfund Site 9L-4 Area
DATES INCLUDED IN SUMMARY
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SUMMARIZED BY FOR CASKINS amp ASSOCIATES INC
55 CAMBRIDGE STREFT SUITE 201 bull BURUNCTON MA oisoa bull TEL 617-273-9030 bull FAX 6i 7-273-9084
77
OSHINSamp Associates Inc
Industrial Hygiene amp Emironmvntal Testing
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Company
LOCATION Salem Acres Superfund Site SL-4 Area
DATES INCLUDED IN SUMMARY J_
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SUMMARIZED BY FOR CASHINS amp ASSOCIATES INC
5 CAMBRIDGE STREET bull SUITE JO I bull BURLINGTON MA 01 K03 TEL ltjl 7-J7J-9080 bull FAX b I 7-273-9084
CASHINS amp Associates Inc
Industrial Hygifnr amp [nvironmenljl res
SERIOUS HAZARD NOTIFICATION
ISSUED TO REPRESENTING
ISSUED BY REPRESENTING CASHINS S ASSOCIATES INcT DAY DATE ISSUED O04Xmdash 1 bull-bullmdashbull f P^JT
PROJECT NAME_ SITE LOCATION
THE PURPOSE OF THE FOLLOWING STATEMENT IS TO DOCUMENT THE EXISTENCE OF A CONDITION OR CONCERN WHICH CASHINS amp ASSOCIATES INC BELIEVES WARRANTS IMMEDIATE CORRECTIVE ACTION POSSIBLE SOLUTIONS AND OR CORRECTIVE ACTIONS WILL BE INCLUDED IN THIS NOTIFICATION WHEN POSSIBLE THIS NOTIFICATION IS LIMITED TO SITUATIONS THAT REPRESENT EITHER IMMEDIATE DANGER TO LIFE OR HEALTH CONDITIONS OR PREVIOUSLY IDENTIFIED CHRONIC PROBLEMS THAT UNDERMINE OUR ABILITY TO EFFECTIVELY INSURE COMPLIANCE WITH THE REQUIREMENTS OF THE HEALTH AND SAFETY PLAN
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55 CAMBRIDGE STREET bull SUITE 201 bull BURLINGTON MA 01 803 bull TEL 61 7-273-9080 bull FAX fgtl 7-273-9084
CISHINS amp Associates Inc
Industrial Hygirne amp Cmimnmtntal Testing
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Company
LOCATION Salem Acres Superfund Site SL-4 Area
DATES INCLUDED IN SUMMARY T
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87161996 1650 6179444882 CASHINS amp ASSOCIATES
CASHINSamp Associates Inc
WEEKLY HEALTH amp SA7STT PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Coqpanv
LOCATION Sa^am Acras Super fund 5 jte SL-4 Area
DATES INCLUDED IN SUMMARY bull
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FOR CASHINS amp ASSOCIATES INC
53 CAMBRIDGE STREET bull SUTE40I bull BURIJSCTON MA 0803 TfL 61 7-273-908O bull FAX fairo-Jshy
07161996 1658 6179444032 CASHINS S ASSOCIATES PAGE 86
CASHINSamp Associates Inc
MtanW HriHtif A
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT ^ mdash
CLIENT T Ford Company
LOCATION Salem Acraa Suoerfund Sita 5L-4
DATES INCLUDED IN SUMMARY bull
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55 CAMBRIDGE STREET bullSUITE 201 bull BURllNCTON MA 01803 bull TEL 617-273-9080 bull FAX 617-273-9084
07161996 1650 617944408 CASHING 3 ASSOCIATES PAGE 05
CASHINSamp Associates Inc
fmimnntattl few
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT t T Ford Coimbanv
LOCATION t Salam Acraa Suoarfund Site SL-4 Arlaquoa
DATES INCLUDED IN SUMMARYj pound mdashiffofrshy f
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SUMMARIZ2D BY _ ampampS FOR CASHINS amp ASSOCIATES INC
55 CAMBRIDGE STREET bull SUITE 201 bull BURLINGTON MA 01803 lt TEL 617-273-9080 bull FAX 617-273-9084
CASHIMS amp ASSOCIATES PAGE 04 07161996 1658 6179444032
OVSHINSamp Associates Inc
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Company T
LOCATION Salem AcrM Suoerfund Stta 8L-4 Araa
DATES INCLUDED IN SUMMARY
(7
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SUMMARIZED BY pound FOR CASHINS amp ASSOCIATES INC
55 CAMBRIDGE STREET bull SUITE 201 bull BURUNGTON MA 01803 bull TEL 617-273-9080 bull FAX 617-273-9084
07161996 1658 6179444082 CASHIMS 3 ASSOCIATES PAGE 03
CASHINSamp Associates Inc
ndurtrW Hrtnm t
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT ^
CLIENT T Ford Company t lP ~ ff2-r
LOCATION Sal era Acraa Suplaquorfund Sj-ta 8L-4 Araa
DATES INCLUDED IN SUMMARY
if
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SUMMARIZED BY FOR CASMINS amp ASSOCIATES INC
55 CAMBRIDGE STREET bull SUITE 201 bull 8URUNGTON MA 01803 bull TEL 617-273-9080 bull FAX 617-273-90W
07151996 18 fO 6179444082 CASHINS S ASSOCIATES PAGE 02
CASHINS amp Associates Inc
WBBKLY HEALTH amp SAFETY FLAK COMPLIANCE SUMMARY REPORT
CLIENT T Ford Compapv
LOCATION i Sal am Acrlaquolaquo Suparfund Sita SL-4 Area
DATES INCLUDED IN SUMMARY i bull pound7 mdash
A 0-3 - A)
SXWMARIZ2D BY FOR CASHINS amp ASSOCIATES INC (
55 CAMBRIDGE STREET SUITE 201 bull SURtlNCTON MA 01803 TEL 617-273-9080 bull FAX 61 7-273-9084
- barcode 14732
- barcodetext SEMS Doc ID 14732
![Page 5: SALEM ACRES SUPERFUND SITE SALEM, MA ...The truck loading pa d consisted of a crushed stone are sea t up along the east sid e o f SL-4 adjacent to the access road A. row of concrete](https://reader036.vdocuments.us/reader036/viewer/2022070114/60729b840fec4e6b4d136a16/html5/thumbnails/5.jpg)
TFCI utilized the site office trailer set-up used by the contractor performing remediation of SL-5 Area (RUST E amp I) TFCI took over the rent and utility charges from DiBiase Realty Trust
The site preparation consisted of constructing a truck loading pad and a decontamination pad improving the access road installation of erosion controls and establishment of work zones
The truck loading pad consisted of a crushed stone area set up along the east side of SL-4 adjacent to the access road A row of concrete Jersey Barriers was set up along the west side of the truck loading pad to contain stockpiled ash and contaminated overburden from spilling on to the pad An excavator was used to load trucks The excavator was able to sit on the stockpiled material behind the Jersey Barriers to load trucks This enabled the operator to carefully load trucks and minimize dust The decontamination pad is discussed in Sec 23
The decontamination pad consisted of an HDPE-lined pad approximately 16 ft wide by 50 ft long The liner was filled with 34 inch crushed stone A sump was constructed to collect rinsate and pump it into a sedimentation tank Heavy timber planks were placed on top of the crushed stone to provide traction for truck tires and prevent rutting of the stone
For dust control TFCI set up a gas-powered high pressure pump capable of 75 gpm at 75 psi The pump fed the network of 2 inch and 1 2 inch flat fire hose with a nozzle for spraying down the work areas
The access road was improved by adding crushed stone as necessary and widening it on both ends of the truck loading and decontamination pads
Erosion controls consisted of silt fence and staked hay bales on the west side of SL-4 adjacent to WA-1 The location of the erosion controls was selected by GEI in conjunction with MADEP and USEPA
The following work zones were established for this site
Exclusion Zone (EZ) Contaminated Reduction Zone (CRZ) Support Zone (SZ)
The limits of these zones were established to conform with the site geometry operational requirements and Health and Safety requirements Initially the EZ was the area within the perimeter boundary of SL-4 except it extended west to the location of the erosion controls The limits of the EZ did not change until all contaminated soil and debris was removed and verified by confirmatory sampling
and testing
The CRZ was established at the top of the slope along the east side of SL-4 The decontamination pad was a major part of the CRZ All worker and equipment decontamination was performed in the CRZ A bootglove washing station was set up in the CRZ along with PPE disposal containers and a handwash PPE was disposed of at Turnkey Landfill in Rochester NH
The Support Zone was established on the east side of the access road opposite SL-4 The office trailer sanitary facilities and water supply were set up in the Support Zone A 2-inch water supply line was temporarily installed under the access road to supply water for decontamination equipment in the CRZ from the water tankers in the SZ
TFCI also initiated a security program to provide full time security watch on site During non-work hours including weekends a security guard was posted in the site trailer The security guard made hourly rounds of the support zone and Access Road including the Barcelona Avenue gate Logs were maintained of security shifts
22 Clearing
Clearing was performed incrementally during the project Trees were cut by chain saw and stockpiled in the Support Zone along the access road Once the majority of trees were cut and stockpiled they were loaded onto 100 cy trailers for off-site disposal Disposal consisted of chipping and burning at a facility in Maine Hauling and disposal was done by Wood Waste of Boston Inc
Phragmites were mixed in with the fly ash during excavation The phragmites constituted a very small portion of the volume of fly ash
23 Decontamination Dust Control and Health and Safety Monitoring
As mentioned above truck loading and decontamination pads were constructed along the east side of the site adjacent to the access road TFCI used a hydraulic excavator to load dump trailers from stockpiles By using an excavator we were able to minimize spillage of material onto the outside of the trailers However all trucks were considered potentially contaminated and were decontaminated by washing down over the decontamination pad
TFCI constructed an overhead spray bar set-up which trucks drove under after loading The wheels and sides of the trucks were then washed down with hoses The decontamination water rinsate was collected in the sump of the HDPE-lined decontamination pad Rinsate was pumped into a 1000 gallon sedimentation tank After removal of the fines the decontamination water was used for dust control
The fly ash was found to be quite dry particularly in the upper 10 to 15 ft and prone to dusting easily TFCI used imported water to keep the fly ash moist in stockpiles and after loading a truck A total of 180000 gallons of water was imported to the site for decontamination and dust control The majority of this water was used for dust control on fly ash The dust control measures employed were quite successful No dust levels were measured exceeding the site criteria at the Barcelona Avenue gate or in the work zones
For Health and Safety Monitoring TFCI contracted with Cashins amp Associates (CA) CA prepared a Health and Safety Plan and performed on-site monitoring of air and noise in the work zone and at the site perimeter A Health and Safety Phase-Out Report prepared by CA is contained in Appendix C
24 Excavation and Loading of Fly Ash
TFCI used two methods for excavating the fly ash and moving it to a stockpile Due to the steep slopes tight quarters and poor traction on the fly ash it was impossible to use a front end loader at the SL-4 site Initially we used an excavator and a bulldozer to excavate and move fly ash to stockpiles
As the mounded area of the fly ash was removed and the excavation began to consist of a steeply sloped face of fly ash we used two excavators The excavators worked as a bucket brigade to excavate and move material up the slope to the stockpile area Material was handled several times to reach the stockpile As the bottom of fly ash level was approached the excavators were able to excavate the fly ash close to the interface between fly ash and contaminated overburden and soilfly ash mixtures
All loading of fly ash was done by an excavator with a large bucket (2 cy capacity) Table 1 summarizes the daily quantities of fly ash loaded In general approximately the same quantity of fly ash was excavated as was loaded each day No significant stockpiles were maintained during the work A stockpile of fly ash excavated on SLshy5 area (by others) was loaded on the first full day of hauling of fly ash from SL-4
25 Excavation and Loading of Contaminated Overburden and SoilFly Ash Mixture
Excavation of contaminated overburden soilfly ash mixture and debris (referred to hereafter as contaminated overburden) was performed using excavators similar to the procedures for fly ash The horizontal limits of excavation were determined by GEI Consultants Inc and are described in the Demonstration of Compliance report prepared by GEI In general the horizontal limits are as follows
Northern - Defined by DA-1 Area Eastern - Defined by confirmatory sampling and analysis along
the Access Road Southern - Defined by SL-5 Area except for Area 1 which was
incorporated into SL-4 site remediation work Western - Defined by WA-1 Area
The bottom of excavation was sampled for confirmatory analysis by GEL The results of this analysis are described in the Demonstration of Compliance Report
Table 2 summarizes the daily quantities of contaminated overburden loaded Approximately the same daily quantity was excavated No significant stockpiles of contaminated overburden were maintained
Where bedrock was encountered contaminated soils were scraped off with the excavator The remaining material was removed as part of bedrock cleaning (see Sec 27) A number of boulders were encountered in the overburden MEC elected to have TFCI decontaminate the boulders on the decontamination pad and then incorporated them into the random fill
26 Ponded Water
Removal of fly ash and contaminated overburden along the western side of SL-4 resulted in a low area which collected both surface water run-off and groundwater seepage This area became a temporary pond containing approximately 100000 to 150000 gallons of water The level fluctuated with the level of the adjoining wetlands
In order to discharge the ponded water to the wetlands (WA-1) the discharge would have to meet Federal drinking water quality standards TFCI arranged for sampling and testing of the ponded water The results are contained in Appendix A Although the water met requirements of USEPA and MADEP for chemical contaminants the water was quite turbid and no practical means of removing suspended solids was available
A request was made to SESD to dispose of the ponded water at its Salem Treatment Facility SESD approved this request on November 20 1995
The ponded water was pumped into conventional septage hauling vehicles on November 27 through 30 1995 A total of 125000 gallons was transported to SESD for disposal Random fill was placed in the low area immediately following pumping of ponded water to avoid collection of additional water
27 Bedrock Cleaning
As required by the Specifications all exposed bedrock was cleaned of all fly ash and
contaminated overburden Several techniques andor methods were used to clean bedrock including
a) Manual broom and shovel work b) Compressor with air gun to loosen material from crevices with water
used for dust control c) A Vac-All truck using water andor compressed air to loosen
material d) A broom attached to the bucket of an excavator
The surface of exposed bedrock was generally quite irregular and required considerable effort to remove soil and fly ash from cracks and crevices In some areas the rock is highly weathered and can be removed In these areas a determination was made in conjunction with GEI as to when to stop removal of weathered bedrock
During placement of random fill and loam some areas of exposed bedrock became re-covered with these earth materials TFCI proposed to topsoil and seed on these areas rather than re-cleaning the bedrock GEI EPA and MEC accepted this proposal
3 SITE RESTORATION
31 Random Fill
Random fill for the site restoration was obtained from a borrow pit located on Munson Street in Peabody MA GEI conducted confirmatory sampling of the borrow source The results are contained in the Demonstration of Compliance Report A grain size analysis is provided in Figure 1 A total of 1176 cy of random fill was delivered to the site and spread over all exposed soil subgrade areas The thickness is 6 inches except along the west side of the site where it ranges up to 5 ft thick where contaminated soil and fly ash were encountered at a deeper level (See Sec 4)
The random fill was spread and compacted using a CAT D4H dozer
32 Loam and Seeding
In the Spring of 1996 after Winter shutdown TFCI placed and spread a 6-inch layer of loam The loam was obtained from a loam stockpile located at a new residential subdivision in Ayer MA called Bennetts Brook and furnished to the site by D amp H Loam Company A total of 695 cy of loam was delivered to the site GEI conducted confirmatory sampling of the loam source The results are contained in the Demonstration of Compliance Report A topsoil analysis report is provided as
Figure 2
The loam was spread using a CAT D4H dozer Areas of the slope where the grade was steeper than 4HIV were first hand-seeded and then covered with Erosion Control and Revegetation Mat (ECRM) The entire loamed area was then hydro-seeded on May 14 1996 The seed used is Massachusetts Highway Department Specification M6030 Slope and Shoulder Mix
33 FencingDemobilization
In order to remove fly ash andor contaminated overburden which extended onto DA-1 it was necessary to remove the fence along the south side of DA-1 After completion of remediation work the fence was replaced Because of the winter shutdown TFCI reinstalled the fence prior to site restoration work to secure the DAshy1 area
Following placement of the random fill TFCI demobilized for winter shutdown Due to an early snowfall it was impossible to loam and seed the site prior to winter shutdown TFCI demobilized equipment and support facilities December 8-13 1995
In the Spring of 1996 it was only necessary to mobilize a dozer and small excavator to place and spread loam
4 QUANTITY SURVEYS AND AS-BUILT PLANS
41 Fly Ash Quantity Survey
In order to calculate the insitu quantity of fly ash for payment TFCI engaged a subcontractor T F Moran for survey work and quantity estimates T F Moran performed an existing conditions topographic survey on April 21 1994 for design studies conducted by GEI Consultants Inc This survey was updated and verified on September 8 1995 by T F Moran for TFCI In addition a stockpile of fly ash removed from SL-5 was also surveyed on this date
T F Moran surveyed the bottom of fly ash on October 18 1995 The results of the fly ash quantity surveys are shown on Figure 3 The quantities of fly ash are as follows
SL-4 Fly Ash 12750 cy SL-5 Fly Ash (stockpiled on SL-4) 520 cv
13270 cy
In addition there was an estimated 1500 cy of fly ash not included in the TF
Moran surveys because the material was in or under active stockpiles at the time of the survey The quantity survey and method of calculation is described in a letter from T F Moran dated January 15 1996 and contained in Appendix B
42 Limits of Remediation
In order to document the limits of remediation T F Moran surveyed the site on November 1 and December 5 1995 Areas where contaminated overburden were removed were surveyed at these times including the limits of exposed bedrock The results of these surveys are shown on Figure 4 The limits of SL-4 site remediation are as follows
Total Site Area Remediated 50860 sf Exposed Ledge 19990 sf
Site Restoration Area 30870 sf
In addition Area 1 is approximately 5416 sf
Note that the total quantity of contaminated overburden and fly ashsoildebris mixture was 6056 tons compared to the estimated 4100 tons from the design studies The primary reasons for the increase include the following
Incorporation of Area 1 from SL-5 in the SL-4 site remediation work
The northern limit of excavation extended further into DA-1 than anticipated in the RA Work Plan
Excavating further west into WA-1 than anticipated in the RA Work Plan
VOC contaminated fly ash and soil in the northwest corner near DAshy1 at a considerable thicknessdepth
The limits of remediation survey are described in the T F Moran letter contained in Appendix B
43 Final As-Built
A final as-built survey was performed by T F Moran on May 21 1996 The results of the survey are shown on Figure 5
TABLE 1 SUMMARY OF ASH REMOVAL
SALEM ACRES SUPERFUND SITE SL-4 AREA
DATE NOMBEraquo0poundLOADS
0AILY TOTAL ifrotfS) i
SEPTS 1 1750
SEPT 1 1 8 13470
SEPT 12 10 21080
SEPT 13 20 45800
SEPT 14 23 50100
SEPT 15 20 43160
SEPT 18 23 46870
SEPT 19 24 54780
SEPT 20 26 52800
SEPT 21 25 47700
SEPT 22 25 46915
SEPT 25 26 51950
SEPT 26 29 56820
SEPT 27 30 55660
SEPT 28 30 58410
SEPT 29 26 53520
OCT2 26 54600
OCT3 26 57000
OCT4 19 41080
OCT5 22 49240
OCT6 26 61860
OCT 10 18 47180
OCT 11 12 33860
OCT 13 17 439 40
OCT 17 3 7600
OCT 19 3 7720
CtnVfOtATIVE TOTAL (TONS)
1750
15220
36300
82100
132200
175360
222230
277010
329810
3775 10
424425
476375
5331 95
5888 55
647265
700785
755385
812385
853465
902705
9645 65
1011745
1045605
1089545
1097145
1104865
TABLE 2 SUMMARY OF CONTAMINATED
OVERBURDEN REMOVAL SALEM ACRES SUPERFUND SITE SL-4 AREA
DATE
on 19 OCT 20
OCT 23
OCT 24
OCT 25
OCT 26
OCT 27
OCT 31
NOV 1
NOV2
NOV 6
NOV 8
NOV 9
NOV 21
NOV 28
DEC 7
NUMBER OF LOADS
14
14
14
13
14
16
18
18
12
4
4
8
8
8
9
2
DAILY TOTAL (TONS)
46121
41649
49314
448 59
46225
48054
62358
56186
491 56
14209
14025
29010
27604
35513
33447
7885
CUMULATIVE TOTAL (TONS)
46121
87770
137084
181943
228168
276222
338580
394766
443922
458131
472156
501166
528770
564283
597730
6056 1 5
- -
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Oct 17 1995 823PM P02 From LTTS OF Mfl INC PHONE No 617 438 S21S
GRftIN SIZE DISTRIBUTION TEST REPORT C c c e
100 i i ^ i i 7 ^ d bdquo bdquo j laquo ii i A j
bdquo9 bdquo
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90 X
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550 gt
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10
0 2Q 0 1SG 100 10 01 aai 00UL
CRflIM CISC - mm
Test X +3 bull4 GRAVEL bull SflMD bull SILT bull DRY uses LL PI
t 16 00 2Z 3 521 256 SC-SM
SIEVE PERCENT FINCR STEVE PERCENT FINCR Uact on Incrwi nuwtoer ilz ilzi bull flUNSON ST PEABODC
bull bull a 96 3 4 777
15 95 10 714 1 92 e 20 607 Descr pt ion
075 90 40 505 bullSILTY CLAYEY GflNO 0 375 34 50 44 4
100 343
3X1 GRAIN SIZE 200 257
8804D60
gtDia Remarks
xC COEFh 1C1CNT5 UTS OF MASSACHUSETTS INC bull
SS1T to 1 u
Pro jlt-r t No UTS OF naSSACHLKKI lgt IMC Project) CftLCM flCHSCC
5 Richardson Lane
GtoneHam Mft 03 IBB Date 101195 Gamn 1 c- No 44fi1A
Figure 1
From UTS OF Mfl INC PHONE No 517 438 6216 Oct 17 1995 824PM F03
SOT ANALYSIS REPORT FOR NEW LAWN 101195
SOIL AND PLANT TISSUE TESTING LABWEST EXPERIMENT STATIONUNIVERSITY OF MASBACIIUfiFTTr AMHERST MA 01003
LAB NUMBER 3951010-107 BAG NUMBER 23467
DATE BFNT f
SOIL FROM COUNTY SOIL WEIGHT 537 g5cn CROP TURFORASS
UTS OF MASS INC COMMENTS ORGANIC MATTER 6 RICHARDSON LANE STONEHAM MA 02180
SAMPLE ID 4461B
LIMESTONE AND FERTILIZER RECOMMCNDATIONS FOR NEW LAWN CONSTRUCTION
No limestone ia required If peat mooc or similar material ia to be incorporated) see enclosed fact sheet
Fertilizer (per 10OO sq ft) 2 1ba N 2 Ibo P2O5 and O 1 bs KZO
Many fertilizer sources and rates may combine to provide acceptable turfgraes establ iahmont either from seed or aod One or two options baaed on this soil teat follow
Incorporate EITHER a 17-23-6 starter fert111zar at 10 lbs1000 sq ft OR a 30-3-3 lawn fertilizer at 7 1b81000 aq ft plus a 0-45-0 (triple superphosphate) fertilizer at 4 lbs1000 aq ft Hnto the top 3 to 4 inches of soil Retest Bull ona year after turf establishment
PLEASE read the enclosed fact sheets for niora specific Information on fertilization and liming procadurea
SOIL pH 71 NITROGEN NO3-N = Oa ppm NH4-N = 5 ppm BUFFER pH 74 ORGANIC MATTER 72 X (Desirable range 4-10X)
NUTRIENT_LEVELS_PPM_| Low Medium High Very High Phosphorus (P) 8 |XXXXXXXXXXXXX Potaaaium (K) 292 [XXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXX Calcium (Ca) 237S XXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXX Magnesium (Mg) 237 JXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXX
CATION EXCII CAP PERCENT BASE SATURATION MICRONUTRIENT LEVELS 130 Meq100g K= 52 Mg=134 Ca=816 ALL NORMAL
CXTRACTABLE ALUMINUM 41 ppm (Soil ranglaquo 10-250 ppm)
The lead level in thio soil 1s low
COMPUTER PROGRAM5-RECOMMENDATIONRbYOtHIOFPtANT~ampSOILSCI UMASS-AMHERST
Figure 2
TARGET SHEET
THE MATERIAL DESCRIBED BELOW WAS NOT SCANNED BECAUSE
(X) OVERSIZED
() NON-PAPER MEDIA
() OTHER
DESCRIPTION DOC 14732 DRAFT FINAL REMEDIAL CONSTRUCTION REPORT FIGURE 3 TOPOGRAPHIC PLAN SL-4 AREA BOTTOM OF FLY ASH SALEM ACRES SHEET 1 OF 1
THE OMITTED MATERIAL IS AVAILABLE FOR REVIEW BY APPOINTMENT
AT THE EPA NEW ENGLAND SUPERFUND RECORDS CENTER BOSTON MA
TARGET SHEET
THE MATERIAL DESCRIBED BELOW WAS NOT SCANNED BECAUSE
(X) OVERSIZED
() NON-PAPER MEDIA
() OTHER
DESCRIPTION DOC 14732 DRAFT FINAL REMEDIAL CONSTRUCTION REPORT FIGURE 4 TOPOGRAPHIC PLAN SL-4 AREA LIMIT OF REMEDIATION SALEM ACRES SHEET 1OF1
THE OMITTED MATERIAL IS AVAILABLE FOR REVIEW BY APPOINTMENT
AT THE EPA NEW ENGLAND SUPERFUND RECORDS CENTER BOSTON MA
TARGET SHEET
THE MATERIAL DESCRIBED BELOW WAS NOT SCANNED BECAUSE
(X) OVERSIZED
() NON-PAPER MEDIA
() OTHER
DESCRIPTION DOC 14732 DRAFT FINAL REMEDIAL CONSTRUCTION REPORT FIGURE 5 TOPOGRAPHIC PLAN SL-4 AREA AS-BUILT PLAN SALEM ACRES SHEET 1 OF 1
THE OMITTED MATERIAL IS AVAILABLE FOR REVIEW BY APPOINTMENT
AT THE EPA NEW ENGLAND SUPERFUND RECORDS CENTER BOSTON MA
(i)
^mft^m
VIEW OF BARCELONA AVENUE THROUGH ENTRANCE GATE PRECONT RUCTION
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(2)
VIEW OF ACCESS ROAD LOOKING NORTH SL-4 ON LEFT PRECONSTRUCTION
VIEW OF ACCESS ROAD LOOKING NORTH SL-4 ON LEFT DA-1 TO LEFT OF PICKUP TRUCK
PRECONSTRUCTION
(3)
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
O ID a CO z O OHI
CO UJ
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(5)
VIEW OF BOUNDARY BETWEEN SL-4 AND DA-1 LOOKING WEST PRECONSTRUCTION
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(6)
EROSION CONTROLS LOOKING NORTH FROM CORNER OF SL-4SL-5 ADJACENT TO WA-1 PRECONSTRUCTION
(7)
TRUCK LOADING PAD LOOKING NORTHWEST FROM SUPPORT ZONE
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(8)
DECONTAMINATION PAD LOOKING NORTHWEST FROM SUPPORT ZONE
(9)
EXCAVATION OF FLY ASH LOOKING NORTHWEST FROM CRZ NOTE WATER FOR DUST CONTROL
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(10)
VIEW LOOKING WEST AFTER REMOVAL OF FLY ASH NOTE WA-1 BEYOND EROSION CONTROLS
(11)
EXCAVATION OF CONTAMINATED OVERBURDEN LOOKING SOUTH FROM DA-1 BOUNDARY
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(12)
VIEW OF RESTORED SITE LOOKING WEST TOWARD WA-1
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VIEW OF RESTORED SITE LOOKING NORTH TOWARD DA-1 ALONG ACCESS ROAD
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(15)
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VIEW OF RESTORED SITE ON DA-1 SJDE OF FENCE - LOOKING ST
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(18)
VIEW OF RESTORED SITE ON DA-1 SIDE OF FENCE - LOOKING WEST SL-4 ON RIGHT
APPENDIX A
ANALYTICAL RESULTS FOR
PONDED WATER
110795 1638 copy617 890 3883 TMA-WALTHAM ] 002007
PRELIMINARY REPORT UNAUDITED RESULTS
Thenno Analytical 300 Second Avenue PO Box 521 Waltham HA 02254
Attn Client Services Phone (617) 890-7200
Cashins amp Associates Order S5-11-034 55 Cambridge Street Date 110795 1522 Burlington HA 01803 Work ID Salem Acres Water
Date Received 110295 Attn Bob Cashins Date Completed
Purchase Order NA Invoice Number Client Code CASHINS
SAMPLE IDENTIFICATION
Sample Sample Number Description 01 11019S-924-01A
Sample Number 04
Sample Description
110195-9Z4-01D 02 110195-924-01B 05 110195-924-01E 03 110195-924-01C
Certified By
110795 1638 copy617 890 3883 TMA-WALTHAM 003007
PRELIMINARY REPORT UNAUDITED RESULTS
Order f S5-11-034 Thermo Analytical Page 2 110795 1522 TEST RESULTS BY SAHPLE
Test Description Volatile Organics- Aqueous Method EPA_8240 Test Code Collected 110195 02-00 Category WATER
DATE INJECTED 110695 DILUTION FACTOR 100 All results reported 1n ugL
COMPOUND RESULT DET LIMIT COMPOUND RESULT
Chloromethane U 10 Broroodi chl oromethane U Vinyl Chloride U 10 2-Chloroethyl Vinyl Ether U
Bromxnethane U 10 4-dethyl -2-pentanone U Chloroethane U 10 c1 3-1 3-Di chl oropropene U
Trichlorofluoronwthane U 50 Tol uene U Acetone 17 10 trans-1 3-Di chl oropropene LI
11-Oichloroethene U 50 11 2-Tri chl oroethane J Carbon Dlsulfide U 50 2-Hexanone U
Methyl ene Chloride U 50 Tetrachl oroethene U 12-Oichloroethene (total) U 50 D1 bromochl oromethane U
11-01 Chloroethane U 50 Chlorobenzene U Vinyl Acetate U 10 Ethyl benzene U
2-Butanone U 10 in and p-Xylene U Chloroform U 50 o-Xylene U
111-Tri Chloroethane U 50 Styrene U Carbon Tetrachlortde U 50 Broraoform U
Benzene U 50 112 2-Tat rachl oroethane U 12-01 Chloroethane U 50 1 3-01 chl orobenzene U
Trichloroethene U 50 I 4-Di chl orobenzene U 12-Dichloropropane U 50 12-01 chl orobenzene U
SURROGATE STANDARDS RESULT LEVEL X RECOVERY
12-Dichloroethane-D4 52 50 104 Toluene-08 47 50 94
l-Bromo-4-fluorobenzene 56 50 112
NOTES AND DEFINITIONS FOR THIS REPORT U =bull Undetected at stated detection limit
VOAJI
OET LIMIT
50 50
10 50 50 50 50 10
5 0 50 5 0 5 0 50 50 50 50 50 50 50 50
110795 1639 copy617 890 3883 TMA-WALTHAM copy004007
PRELIMINARY REPORT UNAUDITED RESULTS
Order t S5-11-034 Thermo Analytical Page 4 110795 1522 TEST RESULTS BY SAMPLE
ianple Description 110195-924-010 Lab No 04A Test Description RCRA Metals 1n Water Method SW846 Test Code
Collected 110195 0200 Category WATER
METAL RESULT DETECTION LIMIT METAL RESULT DETECTION LIMIT
Ag Silver U 10 As Arsenic 870 50
Ba Bar inn B69 10 Pb Lead U 50
Cd Cadmium U 50 Se Sel en1 um Z15 50
Cr Chromi um U 20 Hg Mercury U 020
NOTES AND DEFINITIONS FOR THIS REPORT All results reported in ugL U gt Undetected at stated detection limit
110795 1640 Q617 890 3883 TMA-WALTHAM 0005007
PRELIMINARY REPORT UNAUDITED RESULTS
Order S5-11-034 Thermo Analytical Page 5 110795 1522 REGULAR TEST RESULTS BY TEST
Chemical Oxygen Demand Mlnimun Maximum Method EPA600 4101
Sap Sample Description Result Units Limit Prepared Analyzed By 05A 110195-924-01E 64 bullgL 50 110395 110395 JD
Petroleum Hydrocarbons-H20 Minimum Maximum Method EPA600 4181
Samp Sample Description Result Units Limit Prepared Analyzed By 01A 110195-924-01A 108 mgL 050 110395 110395 JO
110795 1640 reg617 890 3883 TMA-WALTHAM copy006007
PRELIMINARY REPORT UNAUDITED RESULTS
Order I S5-11-034 Therm Analytical Page 6 110795 1522 TEST METHODOLOGIES
USEPA Test Methods for Evaluating Solid Wastes (SUS46 Third Edition) Method 7470 - Preparation of water for Mercury analysis
USEPA Test Methods for Evaluating Solid Vastes (SW846 Third Edition) Method 3010 - Add digestion of aqueous samples and extracts for total metals for analysis by Flame Atomic Absorption Spectroscopy or Inductively Coupled Plasma Spectroscopy
USEPA Test Methods for Evaluating Solid Vastes (SWB46 Third Edition Method 8270 mdash Gas ChroroatographyMass Spectrometry for PAHs
Volatile Organics in Water - Hazardous Substance List
SV846 Method 8240 - Modified
Test Methods for Evaluating Solid Waste SU-846 US EPA Office of Solid Waste and Emergency Response Washington 3rd Edition
Aqueous sanples are analyzed in accordance with Method 8240 using a purge and trap technique followed by 64s ChromatographyMass Spectroscopy
Quality assurance procedures for GCMS Include daily tuning and calibration of the mass spectrometer and the use of surrogate standards in each sample to monitor method performance Quantitatton is performed by the Internal standard method Analysis of blanks duplicate samples and standards are run frequently as further quality assurance procedures
USEPA Test Methods for Evaluating Solid Wastes (SW846 Third Edition) Method 3S10 mdash Separatory Funnel Liquid-Liquid Extraction
EPA-6004-79-020 - Chemical Oxygen Demand - Titrimetric Mid-Level Method 4101
EPA6004-79-020 - Petroleum Hydrocarbons 1n Water Total Recoverable Method 4181 (Spectrophotometric Infrared)
110795 1641 copy617 890 3883 TMA-WALTHAM copy007007
APPENDIX B
QUANTITY SURVEY DOCUMENTATION
TFMORAN INC Surveying - Engineering - Land Planning SoilsWetlands Mapping - Landscape Architecture
January 15 1996
Mr Jack Enos Vice President TFord Company Inc 118 Tenney Street Georgetown MA 01833
RE Survey Results - Salem Acres - SL4 Area Salem Massachusetts
Dear Jack
This letter amends the letter of December 13 1995 per our review last week
TFMoran Inc performed topographic surveys at the Salem Acres site on April 21 1994 for GEI Consultants prior to removal of material and for TFord Company on October 18 1995 after the removal of material The survey data from the original survey in 1994 was adjusted thirty feet higher to correct for a datum difference from current site datum This was due to the original reporting of the Site Benchmark (TP34) elevation as 11464 rather than 14464 which is the correct elevation
Once both topographic surfaces were on the site datum the raw cut volume was obtained by Eaglepoint (Volumes Module) Software utilizing the prismoidal method comparing the two surfaces For reference please see the attached topographic plan which superimposes the October 15 1995 contours (dark lines) over the April 21 1994 contours The volume is based on the intersection of the two surfaces Also it was noted that stock piles of material did exist on site which were not surveyed at the time
The final raw cut volume arrived at by the above methods is 12749 Cubic Yards
In November and December of 1995 the site was resurveyed to locate the area of exposed ledge at the site The results of this survey are shown on the attached topographic worksheet dated November 3 1995 and last revised January 15 1996 The results of the survey indicate the total site area to be 50860 sq ft or 117 acres The total area of exposed ledge surveyed is 19990 sq ft or 46 acres If you have any questions regarding the above call me directly Thank you
Sincerely
John W Myhaver Jr ^_ Field Operations Manager
Enclosure ItorLltr
Route 101 Bedford NH 03110 Phone (603) 472-4488 FAX (603) 472-9747
APPENDIX C
HEALTH AND SAFETY PHASE-OUT REPORT
HEALTH AND SAFETY PHASE-OUT REPORT SALEM ACRES SL-4 AREA
Introduction
During remediation work on SL-4 Health and Safety Monitoring was performed Cashins amp Associates Inc of Reading MA performed the following work as a subcontractor to TFCI
1) Preparation of a site-specific Health and Safety Plan (dated September 1 1995)
2) Provide a Field TechnicianIndustrial Hygienist to serve as Site Safety and Health Officer (SSHO) and to conduct air and noise monitoring
3) Provide a Certified Industrial Hygienist to review Health and Safety and to conduct site specific training (record of training included at end of Appendix C)
4) Collect 8-hour air samples for worker exposure and ambient air at the Barcelona Avenue gate Arrange for analysis of the samples and report results
5) Prepare daily and weekly Health and Safety reports
6) Prepare a Health and Safety Phase-Out Report
In general the following health and safety practices were followed
1) All workers wore hard hats safety glasses work boots gloves and hearing protection as minimum level PPE
2) When working in the exclusion zone workers wore in addition to above tyvek rubber overboots and rubber coated gloves When dust was a potential concern an industrial grade dustmist mask was also worn This level of PPE was considered Level D modified
3) Workers leaving the exclusion zone removed PPE (tyveks gloves boots and masks) in the support zone and either disposed of the items or decontaminated them
4) Workers andor visitors without 40-hour OSHA training were not permitted to enter the exclusion zone
Attached is a report prepared by Cashins amp Associates along with weekly Health and Safety Summary Reports prepared by the Field Hygienist In summary the air monitoring results indicate no levels exceeding the applicable exposure guidelines except one instance
During excavation of contaminated overburden in the northwest comer of the site an area of VOC contaminated soil was encountered Total VOCs levels measured using a PID exceeded the action level established in the Health and Safety Plan The SSHO advised TFCI to upgrade to Level C PPE in order to backfill the excavation in this area TFCI equipment operator upgraded and backfilled the area The SSHO in consultation with the Cashins CIH advised TFCI to avoid work in this area until the contaminants were characterized GEI sampled the material for waste characterization analysis and provided the results to TFCI Based on the results an action level was established by the CIH for the specific contaminants found Further PID measurements indicated levels below the new action level and work was resumed
The noise monitoring indicated that the noise level at the Barcelona Avenue gate was not exceeded Only one instance of excess noise level in the work zone was recorded (10 db(a) above the ambient noise level or 85 db(a)) Workers wore hearing protection in this instance
mdash 07171996 1601 6179444032 CASHIMS S ASSOCIATES PAGE 02
CASHINS amp Associates Inc
ItxhalrM Hy-gifnr A Invtronmtnltl Tttling
July 17 1996
Mr Jack Enos T Ford Company Inc USTenney Street Georgetown MA 01833
Dear Jack
The Site Safety and Health Officer (SSHO) from Cashing amp Associates Inc performed daily inspections of the SL-4 area Salem Acres Superfund Site between 9595 and 12195 in accordance with the Health amp Safety Plan (HSP) for the site Daily inspection logs were submitted every day No accidentsincidents were reported during the work period
In accordance with the Health amp Safety Plan the SSHO performed daily air and noise monitoring at the site during Ac project Samples were collected for metals (lead beryllium chromium arsenic) and Polynuclear Aromatic Hydrocarbons (PAHs) at the site perimeter and for workers exposure determination Coal Tar Pitch Volatiles (a benzene soluble extractables) were also used to determine the workers exposure to PAH compounds Coal Tar Pitch Volatiles (CTPV) were analyzed using OSHA 58 Method If CTPV levels oq personal samples exceed the site criteria of 02 ragm3 the sample was submitted for PAHs analysis All air samples on the site perimeter were analyzed for PAH compounds
Site monitoring air sample collection and results report were done under the supervision of a Certified Industrial Hygienist
Full shift personal worker exposure samples were collected once a week Ambient air samples were collected at the Barcelona Avenue gate about 20 feet to the west of the site gate to determine if site contaminants were migrating off site The ambient air samples were also collected once a week during the project except on rainy days and days without work with contaminated soil
All air samples were analyzed by the American Industrial Hygiene Association accredited ESA Laboratories Inc using the following methods PAHs - NIOSH 5515 Lead - NIOSH 7082 Beryllium - NIOSH 7102 Chromium - NIOSH 7024 Arsenic - NIOSH 7900 Coal Tar Pitch Volatiles - OSHA 58 All methods used are accepted by the industrial hygiene community for 8-hour exposure assessment EPA methods are usually used for ambient air measurements
CRErORTTFOmiOO
80 Mam Street bull Reading MA 01867 bull Phone- 61 7-944-4060 bull Fax 61 7-944-4082
07171996 1601 6179444032 CASHIMS amp ASSOCIATES PAGE 03
The results of air samples for metals and PAHs are presented in Table No 1
All concentrations of metals and PAHs at the site perimeter (Barcelona Avenue) and active work zones were below the OSHA Permissible Exposure Limits (PEL) and the American Conference of Governmental Industrial Hygicnists Threshold Limit Value (ACGIH TLV) Two personal samples collected on October 19 and October 23rd showed Coal Tar Pitch Volatiles (CTPV) results above OSHA PEL and AIHA TLV limits Both samples were resubmittcd to the lab for further analysis to determine if PAH compounds are present because the CTPV results were above site criteria
The results of the PAH concentrations for the personal sample on Mark Goodwin on October 19 1995 during excavation and washing trucks and for the personal sample on Ron Maker on October 23 1995 during excavating and cleaning rocks by compressed air were below OSHA PEL and ACGIH TLV limits
The SSHO performed noise monitoring according to the HSP at the exclusion zone and at the Barcelona Avenue site perimeter fence A Dupont sound level meter was used for noise monitoring The noise level in the exclusion zone during all operations except one did not exceed the on site criteria of 85 dB(a) During a short time when the air compressor had been used to clean rocks the sound level in the exclusion zone next to the air compressor did exceed 85 dB(a) Ear protection devices were worn by the workers during that operation At no time did the noise level at the Barcelona Avenue site perimeter exceed 10 dB(a) above the ambient noise level or 85 dB(a)
The SSHO performed total dust monitoring on a daily basis during the project at the site perimeter downwind of work location and at the site gate using a Miniram real time dust meter The summary of dust monitoring is presented in Table No 2 Total dust concentrations on site and off site did not exceed site criteria of 1 mgm3 and the action level of 05 nigny1
The summary of air monitoring for Volatile Organic Compounds (VOC) is presented in Table No 3 VOC concentrations in the working area did not exceed the on site criteria of 5 ppm in a breathing zone VOC concentrations on the site perimeter did not exceed real time off site criteria of 2 ppm
Five detail reports with results of air sampling were submitted during the project period
Sincerely Cashins amp Associates Inc
Evelina Vaughan Industrial Hygieflfst
CASHINS amp ASSOCIATES Inc
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SITE SPECIFIC amp HAZARD COMMUNICATIONS TRAINING SIGN-IN SHEET
ftt poundpoundpound
DATE
LOCATION OF TRAINING $ALt_M ACu
TIME 9 ^ rW
NAME COMPANY SIGNATURE
40 SALEM ST bull LYNNFIELD MA 011J40 bull TEL 617-2-)5-J77J - FAX ()l7-MS-tUrj
OSHINSamp Associates Inc
Industrill Hygiene amp Environnivnljl fating
SITE SPECIFIC amp HAZARD COMMUNICATIONS TRAINING SIGN-IN SHEET
DATE poundLOCATION OF TRAINING
TIME
NAME COMPANY SIGNATURE
j
40 SAUM ST bull LYNNFIELD MA (J1J40 bull TEL 617-2-T 1773 FAX (gtI7 M5-iU7i
CASHINS amp Associates Inc
Industrie Hygitmt amp tnvironmvnlal
SITE SPECIFIC amp HAZARD COMMUNICATIONS TRAINING SIGN-IN SHEET
DATE
LOCATION OF TRAINING
ir bull vr~ TIME - laquo t bullgt
NAME COMPANY SIGNATURE
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40 SALEM ST bull LYNNFIELD MA 01J40 bull TEL 617-245-J77J bull FAX (gtl7--IS4()rj
89111995 1023 6172733(384 CASHINS ASSOCIATES PAGE 01
CASHINS amp Associates inc
Ifxtuitral Hygltne A fnvironmtnltt Tuning
W3SXLY HBALTH amp SAFETY PLAN COMPLIANCE SUMMARY R3PORT
CLIENT T foyd C o m a n
LOCATION gal era Acres Sx^perfund Site 8L-4 Area
DATES INCLUDED IN SUMMARY
toe
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SUMMARIZED BY FOR CASHINS amp ASSOCIATES INC
55 CAMBRIDGE STREET bull SUITE 201 bull BURLINGTON MA 01803 laquo TEL 61 -273-9080 bull FAX 67-273-9C84
09111995 1023 6172739084 CASHINS ASSOCIATES PAGE 01
CASHINSamp Associates Inc
Induttrml Hygttnr t Emtroomtnttl Ttstinf
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Fprd Company
LOCATION Salen Acres Suoerfund Site SL-4 Area
DATES INCLUDED IN SUMMARY
000 mdash0
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SUMMARIZED BY FOR CASHINS 4 ASSOCIATES INC
55 CAMBRIDGE STREET bull SUITE 201 bull BURLINGTON MA 01803 raquo- TEL 6J 7-273-9080 bull FAX 617-273-9084
CASHINS amp Associates Inc
Industrial Hygitnf amp CmimnmenUl Tinting
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Compan
LOCATION Salem Acres Superfund Site SL-4 Area
DATES INCLUDED IN SUMMARY
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SUMMARIZED BY FOR CASHINS amp ASSOCIATES INC
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CASHING X ASSOCIATES PAGE
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CASHINSamp Associates Inc
WEEKLY HEALTH amp SAFBTT PLAN COMPLIANCE SUMMARY REPORT
CLIENT ^T Ford Combanv
LOCATION Salam Aerag SL-4
DATES INCLUDED IN SUMMARY
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07161996 1650 6179444082 CASH INS amp ASSOCIATES PAGE 08
CASHINSamp Associates Inc
Intutttitl Myffcnt t InvtmnmmUt Itnl
WEEKLY HEALTH 6 SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Fortjl Cqjapany
LOCATION Salem Acrlaquoa Superfund Site 9L-4 Area
DATES INCLUDED IN SUMMARY
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SUMMARIZED BY FOR CASKINS amp ASSOCIATES INC
55 CAMBRIDGE STREFT SUITE 201 bull BURUNCTON MA oisoa bull TEL 617-273-9030 bull FAX 6i 7-273-9084
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OSHINSamp Associates Inc
Industrial Hygiene amp Emironmvntal Testing
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Company
LOCATION Salem Acres Superfund Site SL-4 Area
DATES INCLUDED IN SUMMARY J_
pound0
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SUMMARIZED BY FOR CASHINS amp ASSOCIATES INC
5 CAMBRIDGE STREET bull SUITE JO I bull BURLINGTON MA 01 K03 TEL ltjl 7-J7J-9080 bull FAX b I 7-273-9084
CASHINS amp Associates Inc
Industrial Hygifnr amp [nvironmenljl res
SERIOUS HAZARD NOTIFICATION
ISSUED TO REPRESENTING
ISSUED BY REPRESENTING CASHINS S ASSOCIATES INcT DAY DATE ISSUED O04Xmdash 1 bull-bullmdashbull f P^JT
PROJECT NAME_ SITE LOCATION
THE PURPOSE OF THE FOLLOWING STATEMENT IS TO DOCUMENT THE EXISTENCE OF A CONDITION OR CONCERN WHICH CASHINS amp ASSOCIATES INC BELIEVES WARRANTS IMMEDIATE CORRECTIVE ACTION POSSIBLE SOLUTIONS AND OR CORRECTIVE ACTIONS WILL BE INCLUDED IN THIS NOTIFICATION WHEN POSSIBLE THIS NOTIFICATION IS LIMITED TO SITUATIONS THAT REPRESENT EITHER IMMEDIATE DANGER TO LIFE OR HEALTH CONDITIONS OR PREVIOUSLY IDENTIFIED CHRONIC PROBLEMS THAT UNDERMINE OUR ABILITY TO EFFECTIVELY INSURE COMPLIANCE WITH THE REQUIREMENTS OF THE HEALTH AND SAFETY PLAN
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ACKNOWLEDGEMENT OF RECEIPT OF NOTIFICATION NAMECOMPANY DATE
ACKNOWLEDGEMENT OF ISSUANCE OF NOTIFICATION - NAMECOMPANY ^gt j^f^u^^ CASHINS amp ASSOCINC DATE0 IS
55 CAMBRIDGE STREET bull SUITE 201 bull BURLINGTON MA 01 803 bull TEL 61 7-273-9080 bull FAX fgtl 7-273-9084
CISHINS amp Associates Inc
Industrial Hygirne amp Cmimnmtntal Testing
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Company
LOCATION Salem Acres Superfund Site SL-4 Area
DATES INCLUDED IN SUMMARY T
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87161996 1650 6179444882 CASHINS amp ASSOCIATES
CASHINSamp Associates Inc
WEEKLY HEALTH amp SA7STT PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Coqpanv
LOCATION Sa^am Acras Super fund 5 jte SL-4 Area
DATES INCLUDED IN SUMMARY bull
11 bdquo mdashbull - ampruzpoundtC4 poundLampu ^6zUT
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FOR CASHINS amp ASSOCIATES INC
53 CAMBRIDGE STREET bull SUTE40I bull BURIJSCTON MA 0803 TfL 61 7-273-908O bull FAX fairo-Jshy
07161996 1658 6179444032 CASHINS S ASSOCIATES PAGE 86
CASHINSamp Associates Inc
MtanW HriHtif A
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT ^ mdash
CLIENT T Ford Company
LOCATION Salem Acraa Suoerfund Sita 5L-4
DATES INCLUDED IN SUMMARY bull
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SUMMARIZED BY FOR CASHINS amp ASSOCIATES INC
55 CAMBRIDGE STREET bullSUITE 201 bull BURllNCTON MA 01803 bull TEL 617-273-9080 bull FAX 617-273-9084
07161996 1650 617944408 CASHING 3 ASSOCIATES PAGE 05
CASHINSamp Associates Inc
fmimnntattl few
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT t T Ford Coimbanv
LOCATION t Salam Acraa Suoarfund Site SL-4 Arlaquoa
DATES INCLUDED IN SUMMARYj pound mdashiffofrshy f
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SUMMARIZ2D BY _ ampampS FOR CASHINS amp ASSOCIATES INC
55 CAMBRIDGE STREET bull SUITE 201 bull BURLINGTON MA 01803 lt TEL 617-273-9080 bull FAX 617-273-9084
CASHIMS amp ASSOCIATES PAGE 04 07161996 1658 6179444032
OVSHINSamp Associates Inc
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Company T
LOCATION Salem AcrM Suoerfund Stta 8L-4 Araa
DATES INCLUDED IN SUMMARY
(7
ft ^ 0
SUMMARIZED BY pound FOR CASHINS amp ASSOCIATES INC
55 CAMBRIDGE STREET bull SUITE 201 bull BURUNGTON MA 01803 bull TEL 617-273-9080 bull FAX 617-273-9084
07161996 1658 6179444082 CASHIMS 3 ASSOCIATES PAGE 03
CASHINSamp Associates Inc
ndurtrW Hrtnm t
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT ^
CLIENT T Ford Company t lP ~ ff2-r
LOCATION Sal era Acraa Suplaquorfund Sj-ta 8L-4 Araa
DATES INCLUDED IN SUMMARY
if
j
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SUMMARIZED BY FOR CASMINS amp ASSOCIATES INC
55 CAMBRIDGE STREET bull SUITE 201 bull 8URUNGTON MA 01803 bull TEL 617-273-9080 bull FAX 617-273-90W
07151996 18 fO 6179444082 CASHINS S ASSOCIATES PAGE 02
CASHINS amp Associates Inc
WBBKLY HEALTH amp SAFETY FLAK COMPLIANCE SUMMARY REPORT
CLIENT T Ford Compapv
LOCATION i Sal am Acrlaquolaquo Suparfund Sita SL-4 Area
DATES INCLUDED IN SUMMARY i bull pound7 mdash
A 0-3 - A)
SXWMARIZ2D BY FOR CASHINS amp ASSOCIATES INC (
55 CAMBRIDGE STREET SUITE 201 bull SURtlNCTON MA 01803 TEL 617-273-9080 bull FAX 61 7-273-9084
- barcode 14732
- barcodetext SEMS Doc ID 14732
![Page 6: SALEM ACRES SUPERFUND SITE SALEM, MA ...The truck loading pa d consisted of a crushed stone are sea t up along the east sid e o f SL-4 adjacent to the access road A. row of concrete](https://reader036.vdocuments.us/reader036/viewer/2022070114/60729b840fec4e6b4d136a16/html5/thumbnails/6.jpg)
and testing
The CRZ was established at the top of the slope along the east side of SL-4 The decontamination pad was a major part of the CRZ All worker and equipment decontamination was performed in the CRZ A bootglove washing station was set up in the CRZ along with PPE disposal containers and a handwash PPE was disposed of at Turnkey Landfill in Rochester NH
The Support Zone was established on the east side of the access road opposite SL-4 The office trailer sanitary facilities and water supply were set up in the Support Zone A 2-inch water supply line was temporarily installed under the access road to supply water for decontamination equipment in the CRZ from the water tankers in the SZ
TFCI also initiated a security program to provide full time security watch on site During non-work hours including weekends a security guard was posted in the site trailer The security guard made hourly rounds of the support zone and Access Road including the Barcelona Avenue gate Logs were maintained of security shifts
22 Clearing
Clearing was performed incrementally during the project Trees were cut by chain saw and stockpiled in the Support Zone along the access road Once the majority of trees were cut and stockpiled they were loaded onto 100 cy trailers for off-site disposal Disposal consisted of chipping and burning at a facility in Maine Hauling and disposal was done by Wood Waste of Boston Inc
Phragmites were mixed in with the fly ash during excavation The phragmites constituted a very small portion of the volume of fly ash
23 Decontamination Dust Control and Health and Safety Monitoring
As mentioned above truck loading and decontamination pads were constructed along the east side of the site adjacent to the access road TFCI used a hydraulic excavator to load dump trailers from stockpiles By using an excavator we were able to minimize spillage of material onto the outside of the trailers However all trucks were considered potentially contaminated and were decontaminated by washing down over the decontamination pad
TFCI constructed an overhead spray bar set-up which trucks drove under after loading The wheels and sides of the trucks were then washed down with hoses The decontamination water rinsate was collected in the sump of the HDPE-lined decontamination pad Rinsate was pumped into a 1000 gallon sedimentation tank After removal of the fines the decontamination water was used for dust control
The fly ash was found to be quite dry particularly in the upper 10 to 15 ft and prone to dusting easily TFCI used imported water to keep the fly ash moist in stockpiles and after loading a truck A total of 180000 gallons of water was imported to the site for decontamination and dust control The majority of this water was used for dust control on fly ash The dust control measures employed were quite successful No dust levels were measured exceeding the site criteria at the Barcelona Avenue gate or in the work zones
For Health and Safety Monitoring TFCI contracted with Cashins amp Associates (CA) CA prepared a Health and Safety Plan and performed on-site monitoring of air and noise in the work zone and at the site perimeter A Health and Safety Phase-Out Report prepared by CA is contained in Appendix C
24 Excavation and Loading of Fly Ash
TFCI used two methods for excavating the fly ash and moving it to a stockpile Due to the steep slopes tight quarters and poor traction on the fly ash it was impossible to use a front end loader at the SL-4 site Initially we used an excavator and a bulldozer to excavate and move fly ash to stockpiles
As the mounded area of the fly ash was removed and the excavation began to consist of a steeply sloped face of fly ash we used two excavators The excavators worked as a bucket brigade to excavate and move material up the slope to the stockpile area Material was handled several times to reach the stockpile As the bottom of fly ash level was approached the excavators were able to excavate the fly ash close to the interface between fly ash and contaminated overburden and soilfly ash mixtures
All loading of fly ash was done by an excavator with a large bucket (2 cy capacity) Table 1 summarizes the daily quantities of fly ash loaded In general approximately the same quantity of fly ash was excavated as was loaded each day No significant stockpiles were maintained during the work A stockpile of fly ash excavated on SLshy5 area (by others) was loaded on the first full day of hauling of fly ash from SL-4
25 Excavation and Loading of Contaminated Overburden and SoilFly Ash Mixture
Excavation of contaminated overburden soilfly ash mixture and debris (referred to hereafter as contaminated overburden) was performed using excavators similar to the procedures for fly ash The horizontal limits of excavation were determined by GEI Consultants Inc and are described in the Demonstration of Compliance report prepared by GEI In general the horizontal limits are as follows
Northern - Defined by DA-1 Area Eastern - Defined by confirmatory sampling and analysis along
the Access Road Southern - Defined by SL-5 Area except for Area 1 which was
incorporated into SL-4 site remediation work Western - Defined by WA-1 Area
The bottom of excavation was sampled for confirmatory analysis by GEL The results of this analysis are described in the Demonstration of Compliance Report
Table 2 summarizes the daily quantities of contaminated overburden loaded Approximately the same daily quantity was excavated No significant stockpiles of contaminated overburden were maintained
Where bedrock was encountered contaminated soils were scraped off with the excavator The remaining material was removed as part of bedrock cleaning (see Sec 27) A number of boulders were encountered in the overburden MEC elected to have TFCI decontaminate the boulders on the decontamination pad and then incorporated them into the random fill
26 Ponded Water
Removal of fly ash and contaminated overburden along the western side of SL-4 resulted in a low area which collected both surface water run-off and groundwater seepage This area became a temporary pond containing approximately 100000 to 150000 gallons of water The level fluctuated with the level of the adjoining wetlands
In order to discharge the ponded water to the wetlands (WA-1) the discharge would have to meet Federal drinking water quality standards TFCI arranged for sampling and testing of the ponded water The results are contained in Appendix A Although the water met requirements of USEPA and MADEP for chemical contaminants the water was quite turbid and no practical means of removing suspended solids was available
A request was made to SESD to dispose of the ponded water at its Salem Treatment Facility SESD approved this request on November 20 1995
The ponded water was pumped into conventional septage hauling vehicles on November 27 through 30 1995 A total of 125000 gallons was transported to SESD for disposal Random fill was placed in the low area immediately following pumping of ponded water to avoid collection of additional water
27 Bedrock Cleaning
As required by the Specifications all exposed bedrock was cleaned of all fly ash and
contaminated overburden Several techniques andor methods were used to clean bedrock including
a) Manual broom and shovel work b) Compressor with air gun to loosen material from crevices with water
used for dust control c) A Vac-All truck using water andor compressed air to loosen
material d) A broom attached to the bucket of an excavator
The surface of exposed bedrock was generally quite irregular and required considerable effort to remove soil and fly ash from cracks and crevices In some areas the rock is highly weathered and can be removed In these areas a determination was made in conjunction with GEI as to when to stop removal of weathered bedrock
During placement of random fill and loam some areas of exposed bedrock became re-covered with these earth materials TFCI proposed to topsoil and seed on these areas rather than re-cleaning the bedrock GEI EPA and MEC accepted this proposal
3 SITE RESTORATION
31 Random Fill
Random fill for the site restoration was obtained from a borrow pit located on Munson Street in Peabody MA GEI conducted confirmatory sampling of the borrow source The results are contained in the Demonstration of Compliance Report A grain size analysis is provided in Figure 1 A total of 1176 cy of random fill was delivered to the site and spread over all exposed soil subgrade areas The thickness is 6 inches except along the west side of the site where it ranges up to 5 ft thick where contaminated soil and fly ash were encountered at a deeper level (See Sec 4)
The random fill was spread and compacted using a CAT D4H dozer
32 Loam and Seeding
In the Spring of 1996 after Winter shutdown TFCI placed and spread a 6-inch layer of loam The loam was obtained from a loam stockpile located at a new residential subdivision in Ayer MA called Bennetts Brook and furnished to the site by D amp H Loam Company A total of 695 cy of loam was delivered to the site GEI conducted confirmatory sampling of the loam source The results are contained in the Demonstration of Compliance Report A topsoil analysis report is provided as
Figure 2
The loam was spread using a CAT D4H dozer Areas of the slope where the grade was steeper than 4HIV were first hand-seeded and then covered with Erosion Control and Revegetation Mat (ECRM) The entire loamed area was then hydro-seeded on May 14 1996 The seed used is Massachusetts Highway Department Specification M6030 Slope and Shoulder Mix
33 FencingDemobilization
In order to remove fly ash andor contaminated overburden which extended onto DA-1 it was necessary to remove the fence along the south side of DA-1 After completion of remediation work the fence was replaced Because of the winter shutdown TFCI reinstalled the fence prior to site restoration work to secure the DAshy1 area
Following placement of the random fill TFCI demobilized for winter shutdown Due to an early snowfall it was impossible to loam and seed the site prior to winter shutdown TFCI demobilized equipment and support facilities December 8-13 1995
In the Spring of 1996 it was only necessary to mobilize a dozer and small excavator to place and spread loam
4 QUANTITY SURVEYS AND AS-BUILT PLANS
41 Fly Ash Quantity Survey
In order to calculate the insitu quantity of fly ash for payment TFCI engaged a subcontractor T F Moran for survey work and quantity estimates T F Moran performed an existing conditions topographic survey on April 21 1994 for design studies conducted by GEI Consultants Inc This survey was updated and verified on September 8 1995 by T F Moran for TFCI In addition a stockpile of fly ash removed from SL-5 was also surveyed on this date
T F Moran surveyed the bottom of fly ash on October 18 1995 The results of the fly ash quantity surveys are shown on Figure 3 The quantities of fly ash are as follows
SL-4 Fly Ash 12750 cy SL-5 Fly Ash (stockpiled on SL-4) 520 cv
13270 cy
In addition there was an estimated 1500 cy of fly ash not included in the TF
Moran surveys because the material was in or under active stockpiles at the time of the survey The quantity survey and method of calculation is described in a letter from T F Moran dated January 15 1996 and contained in Appendix B
42 Limits of Remediation
In order to document the limits of remediation T F Moran surveyed the site on November 1 and December 5 1995 Areas where contaminated overburden were removed were surveyed at these times including the limits of exposed bedrock The results of these surveys are shown on Figure 4 The limits of SL-4 site remediation are as follows
Total Site Area Remediated 50860 sf Exposed Ledge 19990 sf
Site Restoration Area 30870 sf
In addition Area 1 is approximately 5416 sf
Note that the total quantity of contaminated overburden and fly ashsoildebris mixture was 6056 tons compared to the estimated 4100 tons from the design studies The primary reasons for the increase include the following
Incorporation of Area 1 from SL-5 in the SL-4 site remediation work
The northern limit of excavation extended further into DA-1 than anticipated in the RA Work Plan
Excavating further west into WA-1 than anticipated in the RA Work Plan
VOC contaminated fly ash and soil in the northwest corner near DAshy1 at a considerable thicknessdepth
The limits of remediation survey are described in the T F Moran letter contained in Appendix B
43 Final As-Built
A final as-built survey was performed by T F Moran on May 21 1996 The results of the survey are shown on Figure 5
TABLE 1 SUMMARY OF ASH REMOVAL
SALEM ACRES SUPERFUND SITE SL-4 AREA
DATE NOMBEraquo0poundLOADS
0AILY TOTAL ifrotfS) i
SEPTS 1 1750
SEPT 1 1 8 13470
SEPT 12 10 21080
SEPT 13 20 45800
SEPT 14 23 50100
SEPT 15 20 43160
SEPT 18 23 46870
SEPT 19 24 54780
SEPT 20 26 52800
SEPT 21 25 47700
SEPT 22 25 46915
SEPT 25 26 51950
SEPT 26 29 56820
SEPT 27 30 55660
SEPT 28 30 58410
SEPT 29 26 53520
OCT2 26 54600
OCT3 26 57000
OCT4 19 41080
OCT5 22 49240
OCT6 26 61860
OCT 10 18 47180
OCT 11 12 33860
OCT 13 17 439 40
OCT 17 3 7600
OCT 19 3 7720
CtnVfOtATIVE TOTAL (TONS)
1750
15220
36300
82100
132200
175360
222230
277010
329810
3775 10
424425
476375
5331 95
5888 55
647265
700785
755385
812385
853465
902705
9645 65
1011745
1045605
1089545
1097145
1104865
TABLE 2 SUMMARY OF CONTAMINATED
OVERBURDEN REMOVAL SALEM ACRES SUPERFUND SITE SL-4 AREA
DATE
on 19 OCT 20
OCT 23
OCT 24
OCT 25
OCT 26
OCT 27
OCT 31
NOV 1
NOV2
NOV 6
NOV 8
NOV 9
NOV 21
NOV 28
DEC 7
NUMBER OF LOADS
14
14
14
13
14
16
18
18
12
4
4
8
8
8
9
2
DAILY TOTAL (TONS)
46121
41649
49314
448 59
46225
48054
62358
56186
491 56
14209
14025
29010
27604
35513
33447
7885
CUMULATIVE TOTAL (TONS)
46121
87770
137084
181943
228168
276222
338580
394766
443922
458131
472156
501166
528770
564283
597730
6056 1 5
- -
--
Oct 17 1995 823PM P02 From LTTS OF Mfl INC PHONE No 617 438 S21S
GRftIN SIZE DISTRIBUTION TEST REPORT C c c e
100 i i ^ i i 7 ^ d bdquo bdquo j laquo ii i A j
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90 X
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550 gt
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CRflIM CISC - mm
Test X +3 bull4 GRAVEL bull SflMD bull SILT bull DRY uses LL PI
t 16 00 2Z 3 521 256 SC-SM
SIEVE PERCENT FINCR STEVE PERCENT FINCR Uact on Incrwi nuwtoer ilz ilzi bull flUNSON ST PEABODC
bull bull a 96 3 4 777
15 95 10 714 1 92 e 20 607 Descr pt ion
075 90 40 505 bullSILTY CLAYEY GflNO 0 375 34 50 44 4
100 343
3X1 GRAIN SIZE 200 257
8804D60
gtDia Remarks
xC COEFh 1C1CNT5 UTS OF MASSACHUSETTS INC bull
SS1T to 1 u
Pro jlt-r t No UTS OF naSSACHLKKI lgt IMC Project) CftLCM flCHSCC
5 Richardson Lane
GtoneHam Mft 03 IBB Date 101195 Gamn 1 c- No 44fi1A
Figure 1
From UTS OF Mfl INC PHONE No 517 438 6216 Oct 17 1995 824PM F03
SOT ANALYSIS REPORT FOR NEW LAWN 101195
SOIL AND PLANT TISSUE TESTING LABWEST EXPERIMENT STATIONUNIVERSITY OF MASBACIIUfiFTTr AMHERST MA 01003
LAB NUMBER 3951010-107 BAG NUMBER 23467
DATE BFNT f
SOIL FROM COUNTY SOIL WEIGHT 537 g5cn CROP TURFORASS
UTS OF MASS INC COMMENTS ORGANIC MATTER 6 RICHARDSON LANE STONEHAM MA 02180
SAMPLE ID 4461B
LIMESTONE AND FERTILIZER RECOMMCNDATIONS FOR NEW LAWN CONSTRUCTION
No limestone ia required If peat mooc or similar material ia to be incorporated) see enclosed fact sheet
Fertilizer (per 10OO sq ft) 2 1ba N 2 Ibo P2O5 and O 1 bs KZO
Many fertilizer sources and rates may combine to provide acceptable turfgraes establ iahmont either from seed or aod One or two options baaed on this soil teat follow
Incorporate EITHER a 17-23-6 starter fert111zar at 10 lbs1000 sq ft OR a 30-3-3 lawn fertilizer at 7 1b81000 aq ft plus a 0-45-0 (triple superphosphate) fertilizer at 4 lbs1000 aq ft Hnto the top 3 to 4 inches of soil Retest Bull ona year after turf establishment
PLEASE read the enclosed fact sheets for niora specific Information on fertilization and liming procadurea
SOIL pH 71 NITROGEN NO3-N = Oa ppm NH4-N = 5 ppm BUFFER pH 74 ORGANIC MATTER 72 X (Desirable range 4-10X)
NUTRIENT_LEVELS_PPM_| Low Medium High Very High Phosphorus (P) 8 |XXXXXXXXXXXXX Potaaaium (K) 292 [XXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXX Calcium (Ca) 237S XXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXX Magnesium (Mg) 237 JXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXX
CATION EXCII CAP PERCENT BASE SATURATION MICRONUTRIENT LEVELS 130 Meq100g K= 52 Mg=134 Ca=816 ALL NORMAL
CXTRACTABLE ALUMINUM 41 ppm (Soil ranglaquo 10-250 ppm)
The lead level in thio soil 1s low
COMPUTER PROGRAM5-RECOMMENDATIONRbYOtHIOFPtANT~ampSOILSCI UMASS-AMHERST
Figure 2
TARGET SHEET
THE MATERIAL DESCRIBED BELOW WAS NOT SCANNED BECAUSE
(X) OVERSIZED
() NON-PAPER MEDIA
() OTHER
DESCRIPTION DOC 14732 DRAFT FINAL REMEDIAL CONSTRUCTION REPORT FIGURE 3 TOPOGRAPHIC PLAN SL-4 AREA BOTTOM OF FLY ASH SALEM ACRES SHEET 1 OF 1
THE OMITTED MATERIAL IS AVAILABLE FOR REVIEW BY APPOINTMENT
AT THE EPA NEW ENGLAND SUPERFUND RECORDS CENTER BOSTON MA
TARGET SHEET
THE MATERIAL DESCRIBED BELOW WAS NOT SCANNED BECAUSE
(X) OVERSIZED
() NON-PAPER MEDIA
() OTHER
DESCRIPTION DOC 14732 DRAFT FINAL REMEDIAL CONSTRUCTION REPORT FIGURE 4 TOPOGRAPHIC PLAN SL-4 AREA LIMIT OF REMEDIATION SALEM ACRES SHEET 1OF1
THE OMITTED MATERIAL IS AVAILABLE FOR REVIEW BY APPOINTMENT
AT THE EPA NEW ENGLAND SUPERFUND RECORDS CENTER BOSTON MA
TARGET SHEET
THE MATERIAL DESCRIBED BELOW WAS NOT SCANNED BECAUSE
(X) OVERSIZED
() NON-PAPER MEDIA
() OTHER
DESCRIPTION DOC 14732 DRAFT FINAL REMEDIAL CONSTRUCTION REPORT FIGURE 5 TOPOGRAPHIC PLAN SL-4 AREA AS-BUILT PLAN SALEM ACRES SHEET 1 OF 1
THE OMITTED MATERIAL IS AVAILABLE FOR REVIEW BY APPOINTMENT
AT THE EPA NEW ENGLAND SUPERFUND RECORDS CENTER BOSTON MA
(i)
^mft^m
VIEW OF BARCELONA AVENUE THROUGH ENTRANCE GATE PRECONT RUCTION
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(2)
VIEW OF ACCESS ROAD LOOKING NORTH SL-4 ON LEFT PRECONSTRUCTION
VIEW OF ACCESS ROAD LOOKING NORTH SL-4 ON LEFT DA-1 TO LEFT OF PICKUP TRUCK
PRECONSTRUCTION
(3)
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
O ID a CO z O OHI
CO UJ
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(5)
VIEW OF BOUNDARY BETWEEN SL-4 AND DA-1 LOOKING WEST PRECONSTRUCTION
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(6)
EROSION CONTROLS LOOKING NORTH FROM CORNER OF SL-4SL-5 ADJACENT TO WA-1 PRECONSTRUCTION
(7)
TRUCK LOADING PAD LOOKING NORTHWEST FROM SUPPORT ZONE
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(8)
DECONTAMINATION PAD LOOKING NORTHWEST FROM SUPPORT ZONE
(9)
EXCAVATION OF FLY ASH LOOKING NORTHWEST FROM CRZ NOTE WATER FOR DUST CONTROL
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(10)
VIEW LOOKING WEST AFTER REMOVAL OF FLY ASH NOTE WA-1 BEYOND EROSION CONTROLS
(11)
EXCAVATION OF CONTAMINATED OVERBURDEN LOOKING SOUTH FROM DA-1 BOUNDARY
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(12)
VIEW OF RESTORED SITE LOOKING WEST TOWARD WA-1
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VIEW OF RESTORED SITE LOOKING NORTH TOWARD DA-1 ALONG ACCESS ROAD
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(15)
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VIEW OF RESTORED SITE ON DA-1 SJDE OF FENCE - LOOKING ST
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(18)
VIEW OF RESTORED SITE ON DA-1 SIDE OF FENCE - LOOKING WEST SL-4 ON RIGHT
APPENDIX A
ANALYTICAL RESULTS FOR
PONDED WATER
110795 1638 copy617 890 3883 TMA-WALTHAM ] 002007
PRELIMINARY REPORT UNAUDITED RESULTS
Thenno Analytical 300 Second Avenue PO Box 521 Waltham HA 02254
Attn Client Services Phone (617) 890-7200
Cashins amp Associates Order S5-11-034 55 Cambridge Street Date 110795 1522 Burlington HA 01803 Work ID Salem Acres Water
Date Received 110295 Attn Bob Cashins Date Completed
Purchase Order NA Invoice Number Client Code CASHINS
SAMPLE IDENTIFICATION
Sample Sample Number Description 01 11019S-924-01A
Sample Number 04
Sample Description
110195-9Z4-01D 02 110195-924-01B 05 110195-924-01E 03 110195-924-01C
Certified By
110795 1638 copy617 890 3883 TMA-WALTHAM 003007
PRELIMINARY REPORT UNAUDITED RESULTS
Order f S5-11-034 Thermo Analytical Page 2 110795 1522 TEST RESULTS BY SAHPLE
Test Description Volatile Organics- Aqueous Method EPA_8240 Test Code Collected 110195 02-00 Category WATER
DATE INJECTED 110695 DILUTION FACTOR 100 All results reported 1n ugL
COMPOUND RESULT DET LIMIT COMPOUND RESULT
Chloromethane U 10 Broroodi chl oromethane U Vinyl Chloride U 10 2-Chloroethyl Vinyl Ether U
Bromxnethane U 10 4-dethyl -2-pentanone U Chloroethane U 10 c1 3-1 3-Di chl oropropene U
Trichlorofluoronwthane U 50 Tol uene U Acetone 17 10 trans-1 3-Di chl oropropene LI
11-Oichloroethene U 50 11 2-Tri chl oroethane J Carbon Dlsulfide U 50 2-Hexanone U
Methyl ene Chloride U 50 Tetrachl oroethene U 12-Oichloroethene (total) U 50 D1 bromochl oromethane U
11-01 Chloroethane U 50 Chlorobenzene U Vinyl Acetate U 10 Ethyl benzene U
2-Butanone U 10 in and p-Xylene U Chloroform U 50 o-Xylene U
111-Tri Chloroethane U 50 Styrene U Carbon Tetrachlortde U 50 Broraoform U
Benzene U 50 112 2-Tat rachl oroethane U 12-01 Chloroethane U 50 1 3-01 chl orobenzene U
Trichloroethene U 50 I 4-Di chl orobenzene U 12-Dichloropropane U 50 12-01 chl orobenzene U
SURROGATE STANDARDS RESULT LEVEL X RECOVERY
12-Dichloroethane-D4 52 50 104 Toluene-08 47 50 94
l-Bromo-4-fluorobenzene 56 50 112
NOTES AND DEFINITIONS FOR THIS REPORT U =bull Undetected at stated detection limit
VOAJI
OET LIMIT
50 50
10 50 50 50 50 10
5 0 50 5 0 5 0 50 50 50 50 50 50 50 50
110795 1639 copy617 890 3883 TMA-WALTHAM copy004007
PRELIMINARY REPORT UNAUDITED RESULTS
Order t S5-11-034 Thermo Analytical Page 4 110795 1522 TEST RESULTS BY SAMPLE
ianple Description 110195-924-010 Lab No 04A Test Description RCRA Metals 1n Water Method SW846 Test Code
Collected 110195 0200 Category WATER
METAL RESULT DETECTION LIMIT METAL RESULT DETECTION LIMIT
Ag Silver U 10 As Arsenic 870 50
Ba Bar inn B69 10 Pb Lead U 50
Cd Cadmium U 50 Se Sel en1 um Z15 50
Cr Chromi um U 20 Hg Mercury U 020
NOTES AND DEFINITIONS FOR THIS REPORT All results reported in ugL U gt Undetected at stated detection limit
110795 1640 Q617 890 3883 TMA-WALTHAM 0005007
PRELIMINARY REPORT UNAUDITED RESULTS
Order S5-11-034 Thermo Analytical Page 5 110795 1522 REGULAR TEST RESULTS BY TEST
Chemical Oxygen Demand Mlnimun Maximum Method EPA600 4101
Sap Sample Description Result Units Limit Prepared Analyzed By 05A 110195-924-01E 64 bullgL 50 110395 110395 JD
Petroleum Hydrocarbons-H20 Minimum Maximum Method EPA600 4181
Samp Sample Description Result Units Limit Prepared Analyzed By 01A 110195-924-01A 108 mgL 050 110395 110395 JO
110795 1640 reg617 890 3883 TMA-WALTHAM copy006007
PRELIMINARY REPORT UNAUDITED RESULTS
Order I S5-11-034 Therm Analytical Page 6 110795 1522 TEST METHODOLOGIES
USEPA Test Methods for Evaluating Solid Wastes (SUS46 Third Edition) Method 7470 - Preparation of water for Mercury analysis
USEPA Test Methods for Evaluating Solid Vastes (SW846 Third Edition) Method 3010 - Add digestion of aqueous samples and extracts for total metals for analysis by Flame Atomic Absorption Spectroscopy or Inductively Coupled Plasma Spectroscopy
USEPA Test Methods for Evaluating Solid Vastes (SWB46 Third Edition Method 8270 mdash Gas ChroroatographyMass Spectrometry for PAHs
Volatile Organics in Water - Hazardous Substance List
SV846 Method 8240 - Modified
Test Methods for Evaluating Solid Waste SU-846 US EPA Office of Solid Waste and Emergency Response Washington 3rd Edition
Aqueous sanples are analyzed in accordance with Method 8240 using a purge and trap technique followed by 64s ChromatographyMass Spectroscopy
Quality assurance procedures for GCMS Include daily tuning and calibration of the mass spectrometer and the use of surrogate standards in each sample to monitor method performance Quantitatton is performed by the Internal standard method Analysis of blanks duplicate samples and standards are run frequently as further quality assurance procedures
USEPA Test Methods for Evaluating Solid Wastes (SW846 Third Edition) Method 3S10 mdash Separatory Funnel Liquid-Liquid Extraction
EPA-6004-79-020 - Chemical Oxygen Demand - Titrimetric Mid-Level Method 4101
EPA6004-79-020 - Petroleum Hydrocarbons 1n Water Total Recoverable Method 4181 (Spectrophotometric Infrared)
110795 1641 copy617 890 3883 TMA-WALTHAM copy007007
APPENDIX B
QUANTITY SURVEY DOCUMENTATION
TFMORAN INC Surveying - Engineering - Land Planning SoilsWetlands Mapping - Landscape Architecture
January 15 1996
Mr Jack Enos Vice President TFord Company Inc 118 Tenney Street Georgetown MA 01833
RE Survey Results - Salem Acres - SL4 Area Salem Massachusetts
Dear Jack
This letter amends the letter of December 13 1995 per our review last week
TFMoran Inc performed topographic surveys at the Salem Acres site on April 21 1994 for GEI Consultants prior to removal of material and for TFord Company on October 18 1995 after the removal of material The survey data from the original survey in 1994 was adjusted thirty feet higher to correct for a datum difference from current site datum This was due to the original reporting of the Site Benchmark (TP34) elevation as 11464 rather than 14464 which is the correct elevation
Once both topographic surfaces were on the site datum the raw cut volume was obtained by Eaglepoint (Volumes Module) Software utilizing the prismoidal method comparing the two surfaces For reference please see the attached topographic plan which superimposes the October 15 1995 contours (dark lines) over the April 21 1994 contours The volume is based on the intersection of the two surfaces Also it was noted that stock piles of material did exist on site which were not surveyed at the time
The final raw cut volume arrived at by the above methods is 12749 Cubic Yards
In November and December of 1995 the site was resurveyed to locate the area of exposed ledge at the site The results of this survey are shown on the attached topographic worksheet dated November 3 1995 and last revised January 15 1996 The results of the survey indicate the total site area to be 50860 sq ft or 117 acres The total area of exposed ledge surveyed is 19990 sq ft or 46 acres If you have any questions regarding the above call me directly Thank you
Sincerely
John W Myhaver Jr ^_ Field Operations Manager
Enclosure ItorLltr
Route 101 Bedford NH 03110 Phone (603) 472-4488 FAX (603) 472-9747
APPENDIX C
HEALTH AND SAFETY PHASE-OUT REPORT
HEALTH AND SAFETY PHASE-OUT REPORT SALEM ACRES SL-4 AREA
Introduction
During remediation work on SL-4 Health and Safety Monitoring was performed Cashins amp Associates Inc of Reading MA performed the following work as a subcontractor to TFCI
1) Preparation of a site-specific Health and Safety Plan (dated September 1 1995)
2) Provide a Field TechnicianIndustrial Hygienist to serve as Site Safety and Health Officer (SSHO) and to conduct air and noise monitoring
3) Provide a Certified Industrial Hygienist to review Health and Safety and to conduct site specific training (record of training included at end of Appendix C)
4) Collect 8-hour air samples for worker exposure and ambient air at the Barcelona Avenue gate Arrange for analysis of the samples and report results
5) Prepare daily and weekly Health and Safety reports
6) Prepare a Health and Safety Phase-Out Report
In general the following health and safety practices were followed
1) All workers wore hard hats safety glasses work boots gloves and hearing protection as minimum level PPE
2) When working in the exclusion zone workers wore in addition to above tyvek rubber overboots and rubber coated gloves When dust was a potential concern an industrial grade dustmist mask was also worn This level of PPE was considered Level D modified
3) Workers leaving the exclusion zone removed PPE (tyveks gloves boots and masks) in the support zone and either disposed of the items or decontaminated them
4) Workers andor visitors without 40-hour OSHA training were not permitted to enter the exclusion zone
Attached is a report prepared by Cashins amp Associates along with weekly Health and Safety Summary Reports prepared by the Field Hygienist In summary the air monitoring results indicate no levels exceeding the applicable exposure guidelines except one instance
During excavation of contaminated overburden in the northwest comer of the site an area of VOC contaminated soil was encountered Total VOCs levels measured using a PID exceeded the action level established in the Health and Safety Plan The SSHO advised TFCI to upgrade to Level C PPE in order to backfill the excavation in this area TFCI equipment operator upgraded and backfilled the area The SSHO in consultation with the Cashins CIH advised TFCI to avoid work in this area until the contaminants were characterized GEI sampled the material for waste characterization analysis and provided the results to TFCI Based on the results an action level was established by the CIH for the specific contaminants found Further PID measurements indicated levels below the new action level and work was resumed
The noise monitoring indicated that the noise level at the Barcelona Avenue gate was not exceeded Only one instance of excess noise level in the work zone was recorded (10 db(a) above the ambient noise level or 85 db(a)) Workers wore hearing protection in this instance
mdash 07171996 1601 6179444032 CASHIMS S ASSOCIATES PAGE 02
CASHINS amp Associates Inc
ItxhalrM Hy-gifnr A Invtronmtnltl Tttling
July 17 1996
Mr Jack Enos T Ford Company Inc USTenney Street Georgetown MA 01833
Dear Jack
The Site Safety and Health Officer (SSHO) from Cashing amp Associates Inc performed daily inspections of the SL-4 area Salem Acres Superfund Site between 9595 and 12195 in accordance with the Health amp Safety Plan (HSP) for the site Daily inspection logs were submitted every day No accidentsincidents were reported during the work period
In accordance with the Health amp Safety Plan the SSHO performed daily air and noise monitoring at the site during Ac project Samples were collected for metals (lead beryllium chromium arsenic) and Polynuclear Aromatic Hydrocarbons (PAHs) at the site perimeter and for workers exposure determination Coal Tar Pitch Volatiles (a benzene soluble extractables) were also used to determine the workers exposure to PAH compounds Coal Tar Pitch Volatiles (CTPV) were analyzed using OSHA 58 Method If CTPV levels oq personal samples exceed the site criteria of 02 ragm3 the sample was submitted for PAHs analysis All air samples on the site perimeter were analyzed for PAH compounds
Site monitoring air sample collection and results report were done under the supervision of a Certified Industrial Hygienist
Full shift personal worker exposure samples were collected once a week Ambient air samples were collected at the Barcelona Avenue gate about 20 feet to the west of the site gate to determine if site contaminants were migrating off site The ambient air samples were also collected once a week during the project except on rainy days and days without work with contaminated soil
All air samples were analyzed by the American Industrial Hygiene Association accredited ESA Laboratories Inc using the following methods PAHs - NIOSH 5515 Lead - NIOSH 7082 Beryllium - NIOSH 7102 Chromium - NIOSH 7024 Arsenic - NIOSH 7900 Coal Tar Pitch Volatiles - OSHA 58 All methods used are accepted by the industrial hygiene community for 8-hour exposure assessment EPA methods are usually used for ambient air measurements
CRErORTTFOmiOO
80 Mam Street bull Reading MA 01867 bull Phone- 61 7-944-4060 bull Fax 61 7-944-4082
07171996 1601 6179444032 CASHIMS amp ASSOCIATES PAGE 03
The results of air samples for metals and PAHs are presented in Table No 1
All concentrations of metals and PAHs at the site perimeter (Barcelona Avenue) and active work zones were below the OSHA Permissible Exposure Limits (PEL) and the American Conference of Governmental Industrial Hygicnists Threshold Limit Value (ACGIH TLV) Two personal samples collected on October 19 and October 23rd showed Coal Tar Pitch Volatiles (CTPV) results above OSHA PEL and AIHA TLV limits Both samples were resubmittcd to the lab for further analysis to determine if PAH compounds are present because the CTPV results were above site criteria
The results of the PAH concentrations for the personal sample on Mark Goodwin on October 19 1995 during excavation and washing trucks and for the personal sample on Ron Maker on October 23 1995 during excavating and cleaning rocks by compressed air were below OSHA PEL and ACGIH TLV limits
The SSHO performed noise monitoring according to the HSP at the exclusion zone and at the Barcelona Avenue site perimeter fence A Dupont sound level meter was used for noise monitoring The noise level in the exclusion zone during all operations except one did not exceed the on site criteria of 85 dB(a) During a short time when the air compressor had been used to clean rocks the sound level in the exclusion zone next to the air compressor did exceed 85 dB(a) Ear protection devices were worn by the workers during that operation At no time did the noise level at the Barcelona Avenue site perimeter exceed 10 dB(a) above the ambient noise level or 85 dB(a)
The SSHO performed total dust monitoring on a daily basis during the project at the site perimeter downwind of work location and at the site gate using a Miniram real time dust meter The summary of dust monitoring is presented in Table No 2 Total dust concentrations on site and off site did not exceed site criteria of 1 mgm3 and the action level of 05 nigny1
The summary of air monitoring for Volatile Organic Compounds (VOC) is presented in Table No 3 VOC concentrations in the working area did not exceed the on site criteria of 5 ppm in a breathing zone VOC concentrations on the site perimeter did not exceed real time off site criteria of 2 ppm
Five detail reports with results of air sampling were submitted during the project period
Sincerely Cashins amp Associates Inc
Evelina Vaughan Industrial Hygieflfst
CASHINS amp ASSOCIATES Inc
80 Mam Street bull Reading MA 01867 bull Phone61 7-944-4060 bull Fax 617-944-4082
07171996 1601 6179444082 CASHINS S ASSOCIATES PAGE 04
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89111995 1023 6172733(384 CASHINS ASSOCIATES PAGE 01
CASHINS amp Associates inc
Ifxtuitral Hygltne A fnvironmtnltt Tuning
W3SXLY HBALTH amp SAFETY PLAN COMPLIANCE SUMMARY R3PORT
CLIENT T foyd C o m a n
LOCATION gal era Acres Sx^perfund Site 8L-4 Area
DATES INCLUDED IN SUMMARY
toe
-
SUMMARIZED BY FOR CASHINS amp ASSOCIATES INC
55 CAMBRIDGE STREET bull SUITE 201 bull BURLINGTON MA 01803 laquo TEL 61 -273-9080 bull FAX 67-273-9C84
09111995 1023 6172739084 CASHINS ASSOCIATES PAGE 01
CASHINSamp Associates Inc
Induttrml Hygttnr t Emtroomtnttl Ttstinf
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Fprd Company
LOCATION Salen Acres Suoerfund Site SL-4 Area
DATES INCLUDED IN SUMMARY
000 mdash0
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I
SUMMARIZED BY FOR CASHINS 4 ASSOCIATES INC
55 CAMBRIDGE STREET bull SUITE 201 bull BURLINGTON MA 01803 raquo- TEL 6J 7-273-9080 bull FAX 617-273-9084
CASHINS amp Associates Inc
Industrial Hygitnf amp CmimnmenUl Tinting
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Compan
LOCATION Salem Acres Superfund Site SL-4 Area
DATES INCLUDED IN SUMMARY
-amp
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tu bull lts fffr-t TC mdash
bull amppoundf-te
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55 CAMBRIDGE STREET SUTE20 bull BLRLINCTON MA 01803 TEL-b l 7-273-9080 bull FAX 61 r-~3-084
CASHING X ASSOCIATES PAGE
1C n -044408shy07161336 1650 61 344408shy
CASHINSamp Associates Inc
WEEKLY HEALTH amp SAFBTT PLAN COMPLIANCE SUMMARY REPORT
CLIENT ^T Ford Combanv
LOCATION Salam Aerag SL-4
DATES INCLUDED IN SUMMARY
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55 CAMBRIDGE STREET bull SUITE 201 bull SURUNCTON vu 01803 TEL 61 rori-^oao FAX 61 ~ rj
07161996 1650 6179444082 CASHI MS amp ASSOCIATES PAGE 10
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DATES INCLUDED IN BUNKARY)
CA5HIN3 i AH30CIATES INC
55 CAM8RJDCpound STWET bull SUTTE201 eolaquolNCTONMAOJlaquo03 TIL 6t7shy
07161996 1650 6179444082 CASH INS amp ASSOCIATES PAGE 08
CASHINSamp Associates Inc
Intutttitl Myffcnt t InvtmnmmUt Itnl
WEEKLY HEALTH 6 SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Fortjl Cqjapany
LOCATION Salem Acrlaquoa Superfund Site 9L-4 Area
DATES INCLUDED IN SUMMARY
s
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SUMMARIZED BY FOR CASKINS amp ASSOCIATES INC
55 CAMBRIDGE STREFT SUITE 201 bull BURUNCTON MA oisoa bull TEL 617-273-9030 bull FAX 6i 7-273-9084
77
OSHINSamp Associates Inc
Industrial Hygiene amp Emironmvntal Testing
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Company
LOCATION Salem Acres Superfund Site SL-4 Area
DATES INCLUDED IN SUMMARY J_
pound0
77
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SUMMARIZED BY FOR CASHINS amp ASSOCIATES INC
5 CAMBRIDGE STREET bull SUITE JO I bull BURLINGTON MA 01 K03 TEL ltjl 7-J7J-9080 bull FAX b I 7-273-9084
CASHINS amp Associates Inc
Industrial Hygifnr amp [nvironmenljl res
SERIOUS HAZARD NOTIFICATION
ISSUED TO REPRESENTING
ISSUED BY REPRESENTING CASHINS S ASSOCIATES INcT DAY DATE ISSUED O04Xmdash 1 bull-bullmdashbull f P^JT
PROJECT NAME_ SITE LOCATION
THE PURPOSE OF THE FOLLOWING STATEMENT IS TO DOCUMENT THE EXISTENCE OF A CONDITION OR CONCERN WHICH CASHINS amp ASSOCIATES INC BELIEVES WARRANTS IMMEDIATE CORRECTIVE ACTION POSSIBLE SOLUTIONS AND OR CORRECTIVE ACTIONS WILL BE INCLUDED IN THIS NOTIFICATION WHEN POSSIBLE THIS NOTIFICATION IS LIMITED TO SITUATIONS THAT REPRESENT EITHER IMMEDIATE DANGER TO LIFE OR HEALTH CONDITIONS OR PREVIOUSLY IDENTIFIED CHRONIC PROBLEMS THAT UNDERMINE OUR ABILITY TO EFFECTIVELY INSURE COMPLIANCE WITH THE REQUIREMENTS OF THE HEALTH AND SAFETY PLAN
0
TLc ic^ricj^r
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f P U_ -L AM - fshy V mdash [T T
ACKNOWLEDGEMENT OF RECEIPT OF NOTIFICATION NAMECOMPANY DATE
ACKNOWLEDGEMENT OF ISSUANCE OF NOTIFICATION - NAMECOMPANY ^gt j^f^u^^ CASHINS amp ASSOCINC DATE0 IS
55 CAMBRIDGE STREET bull SUITE 201 bull BURLINGTON MA 01 803 bull TEL 61 7-273-9080 bull FAX fgtl 7-273-9084
CISHINS amp Associates Inc
Industrial Hygirne amp Cmimnmtntal Testing
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Company
LOCATION Salem Acres Superfund Site SL-4 Area
DATES INCLUDED IN SUMMARY T
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CASHINSamp Associates Inc
WEEKLY HEALTH amp SA7STT PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Coqpanv
LOCATION Sa^am Acras Super fund 5 jte SL-4 Area
DATES INCLUDED IN SUMMARY bull
11 bdquo mdashbull - ampruzpoundtC4 poundLampu ^6zUT
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FOR CASHINS amp ASSOCIATES INC
53 CAMBRIDGE STREET bull SUTE40I bull BURIJSCTON MA 0803 TfL 61 7-273-908O bull FAX fairo-Jshy
07161996 1658 6179444032 CASHINS S ASSOCIATES PAGE 86
CASHINSamp Associates Inc
MtanW HriHtif A
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT ^ mdash
CLIENT T Ford Company
LOCATION Salem Acraa Suoerfund Sita 5L-4
DATES INCLUDED IN SUMMARY bull
6 03 HL fro- TH4-shy
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SUMMARIZED BY FOR CASHINS amp ASSOCIATES INC
55 CAMBRIDGE STREET bullSUITE 201 bull BURllNCTON MA 01803 bull TEL 617-273-9080 bull FAX 617-273-9084
07161996 1650 617944408 CASHING 3 ASSOCIATES PAGE 05
CASHINSamp Associates Inc
fmimnntattl few
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT t T Ford Coimbanv
LOCATION t Salam Acraa Suoarfund Site SL-4 Arlaquoa
DATES INCLUDED IN SUMMARYj pound mdashiffofrshy f
K (J
-ficuts O
SUMMARIZ2D BY _ ampampS FOR CASHINS amp ASSOCIATES INC
55 CAMBRIDGE STREET bull SUITE 201 bull BURLINGTON MA 01803 lt TEL 617-273-9080 bull FAX 617-273-9084
CASHIMS amp ASSOCIATES PAGE 04 07161996 1658 6179444032
OVSHINSamp Associates Inc
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Company T
LOCATION Salem AcrM Suoerfund Stta 8L-4 Araa
DATES INCLUDED IN SUMMARY
(7
ft ^ 0
SUMMARIZED BY pound FOR CASHINS amp ASSOCIATES INC
55 CAMBRIDGE STREET bull SUITE 201 bull BURUNGTON MA 01803 bull TEL 617-273-9080 bull FAX 617-273-9084
07161996 1658 6179444082 CASHIMS 3 ASSOCIATES PAGE 03
CASHINSamp Associates Inc
ndurtrW Hrtnm t
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT ^
CLIENT T Ford Company t lP ~ ff2-r
LOCATION Sal era Acraa Suplaquorfund Sj-ta 8L-4 Araa
DATES INCLUDED IN SUMMARY
if
j
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SUMMARIZED BY FOR CASMINS amp ASSOCIATES INC
55 CAMBRIDGE STREET bull SUITE 201 bull 8URUNGTON MA 01803 bull TEL 617-273-9080 bull FAX 617-273-90W
07151996 18 fO 6179444082 CASHINS S ASSOCIATES PAGE 02
CASHINS amp Associates Inc
WBBKLY HEALTH amp SAFETY FLAK COMPLIANCE SUMMARY REPORT
CLIENT T Ford Compapv
LOCATION i Sal am Acrlaquolaquo Suparfund Sita SL-4 Area
DATES INCLUDED IN SUMMARY i bull pound7 mdash
A 0-3 - A)
SXWMARIZ2D BY FOR CASHINS amp ASSOCIATES INC (
55 CAMBRIDGE STREET SUITE 201 bull SURtlNCTON MA 01803 TEL 617-273-9080 bull FAX 61 7-273-9084
- barcode 14732
- barcodetext SEMS Doc ID 14732
![Page 7: SALEM ACRES SUPERFUND SITE SALEM, MA ...The truck loading pa d consisted of a crushed stone are sea t up along the east sid e o f SL-4 adjacent to the access road A. row of concrete](https://reader036.vdocuments.us/reader036/viewer/2022070114/60729b840fec4e6b4d136a16/html5/thumbnails/7.jpg)
The fly ash was found to be quite dry particularly in the upper 10 to 15 ft and prone to dusting easily TFCI used imported water to keep the fly ash moist in stockpiles and after loading a truck A total of 180000 gallons of water was imported to the site for decontamination and dust control The majority of this water was used for dust control on fly ash The dust control measures employed were quite successful No dust levels were measured exceeding the site criteria at the Barcelona Avenue gate or in the work zones
For Health and Safety Monitoring TFCI contracted with Cashins amp Associates (CA) CA prepared a Health and Safety Plan and performed on-site monitoring of air and noise in the work zone and at the site perimeter A Health and Safety Phase-Out Report prepared by CA is contained in Appendix C
24 Excavation and Loading of Fly Ash
TFCI used two methods for excavating the fly ash and moving it to a stockpile Due to the steep slopes tight quarters and poor traction on the fly ash it was impossible to use a front end loader at the SL-4 site Initially we used an excavator and a bulldozer to excavate and move fly ash to stockpiles
As the mounded area of the fly ash was removed and the excavation began to consist of a steeply sloped face of fly ash we used two excavators The excavators worked as a bucket brigade to excavate and move material up the slope to the stockpile area Material was handled several times to reach the stockpile As the bottom of fly ash level was approached the excavators were able to excavate the fly ash close to the interface between fly ash and contaminated overburden and soilfly ash mixtures
All loading of fly ash was done by an excavator with a large bucket (2 cy capacity) Table 1 summarizes the daily quantities of fly ash loaded In general approximately the same quantity of fly ash was excavated as was loaded each day No significant stockpiles were maintained during the work A stockpile of fly ash excavated on SLshy5 area (by others) was loaded on the first full day of hauling of fly ash from SL-4
25 Excavation and Loading of Contaminated Overburden and SoilFly Ash Mixture
Excavation of contaminated overburden soilfly ash mixture and debris (referred to hereafter as contaminated overburden) was performed using excavators similar to the procedures for fly ash The horizontal limits of excavation were determined by GEI Consultants Inc and are described in the Demonstration of Compliance report prepared by GEI In general the horizontal limits are as follows
Northern - Defined by DA-1 Area Eastern - Defined by confirmatory sampling and analysis along
the Access Road Southern - Defined by SL-5 Area except for Area 1 which was
incorporated into SL-4 site remediation work Western - Defined by WA-1 Area
The bottom of excavation was sampled for confirmatory analysis by GEL The results of this analysis are described in the Demonstration of Compliance Report
Table 2 summarizes the daily quantities of contaminated overburden loaded Approximately the same daily quantity was excavated No significant stockpiles of contaminated overburden were maintained
Where bedrock was encountered contaminated soils were scraped off with the excavator The remaining material was removed as part of bedrock cleaning (see Sec 27) A number of boulders were encountered in the overburden MEC elected to have TFCI decontaminate the boulders on the decontamination pad and then incorporated them into the random fill
26 Ponded Water
Removal of fly ash and contaminated overburden along the western side of SL-4 resulted in a low area which collected both surface water run-off and groundwater seepage This area became a temporary pond containing approximately 100000 to 150000 gallons of water The level fluctuated with the level of the adjoining wetlands
In order to discharge the ponded water to the wetlands (WA-1) the discharge would have to meet Federal drinking water quality standards TFCI arranged for sampling and testing of the ponded water The results are contained in Appendix A Although the water met requirements of USEPA and MADEP for chemical contaminants the water was quite turbid and no practical means of removing suspended solids was available
A request was made to SESD to dispose of the ponded water at its Salem Treatment Facility SESD approved this request on November 20 1995
The ponded water was pumped into conventional septage hauling vehicles on November 27 through 30 1995 A total of 125000 gallons was transported to SESD for disposal Random fill was placed in the low area immediately following pumping of ponded water to avoid collection of additional water
27 Bedrock Cleaning
As required by the Specifications all exposed bedrock was cleaned of all fly ash and
contaminated overburden Several techniques andor methods were used to clean bedrock including
a) Manual broom and shovel work b) Compressor with air gun to loosen material from crevices with water
used for dust control c) A Vac-All truck using water andor compressed air to loosen
material d) A broom attached to the bucket of an excavator
The surface of exposed bedrock was generally quite irregular and required considerable effort to remove soil and fly ash from cracks and crevices In some areas the rock is highly weathered and can be removed In these areas a determination was made in conjunction with GEI as to when to stop removal of weathered bedrock
During placement of random fill and loam some areas of exposed bedrock became re-covered with these earth materials TFCI proposed to topsoil and seed on these areas rather than re-cleaning the bedrock GEI EPA and MEC accepted this proposal
3 SITE RESTORATION
31 Random Fill
Random fill for the site restoration was obtained from a borrow pit located on Munson Street in Peabody MA GEI conducted confirmatory sampling of the borrow source The results are contained in the Demonstration of Compliance Report A grain size analysis is provided in Figure 1 A total of 1176 cy of random fill was delivered to the site and spread over all exposed soil subgrade areas The thickness is 6 inches except along the west side of the site where it ranges up to 5 ft thick where contaminated soil and fly ash were encountered at a deeper level (See Sec 4)
The random fill was spread and compacted using a CAT D4H dozer
32 Loam and Seeding
In the Spring of 1996 after Winter shutdown TFCI placed and spread a 6-inch layer of loam The loam was obtained from a loam stockpile located at a new residential subdivision in Ayer MA called Bennetts Brook and furnished to the site by D amp H Loam Company A total of 695 cy of loam was delivered to the site GEI conducted confirmatory sampling of the loam source The results are contained in the Demonstration of Compliance Report A topsoil analysis report is provided as
Figure 2
The loam was spread using a CAT D4H dozer Areas of the slope where the grade was steeper than 4HIV were first hand-seeded and then covered with Erosion Control and Revegetation Mat (ECRM) The entire loamed area was then hydro-seeded on May 14 1996 The seed used is Massachusetts Highway Department Specification M6030 Slope and Shoulder Mix
33 FencingDemobilization
In order to remove fly ash andor contaminated overburden which extended onto DA-1 it was necessary to remove the fence along the south side of DA-1 After completion of remediation work the fence was replaced Because of the winter shutdown TFCI reinstalled the fence prior to site restoration work to secure the DAshy1 area
Following placement of the random fill TFCI demobilized for winter shutdown Due to an early snowfall it was impossible to loam and seed the site prior to winter shutdown TFCI demobilized equipment and support facilities December 8-13 1995
In the Spring of 1996 it was only necessary to mobilize a dozer and small excavator to place and spread loam
4 QUANTITY SURVEYS AND AS-BUILT PLANS
41 Fly Ash Quantity Survey
In order to calculate the insitu quantity of fly ash for payment TFCI engaged a subcontractor T F Moran for survey work and quantity estimates T F Moran performed an existing conditions topographic survey on April 21 1994 for design studies conducted by GEI Consultants Inc This survey was updated and verified on September 8 1995 by T F Moran for TFCI In addition a stockpile of fly ash removed from SL-5 was also surveyed on this date
T F Moran surveyed the bottom of fly ash on October 18 1995 The results of the fly ash quantity surveys are shown on Figure 3 The quantities of fly ash are as follows
SL-4 Fly Ash 12750 cy SL-5 Fly Ash (stockpiled on SL-4) 520 cv
13270 cy
In addition there was an estimated 1500 cy of fly ash not included in the TF
Moran surveys because the material was in or under active stockpiles at the time of the survey The quantity survey and method of calculation is described in a letter from T F Moran dated January 15 1996 and contained in Appendix B
42 Limits of Remediation
In order to document the limits of remediation T F Moran surveyed the site on November 1 and December 5 1995 Areas where contaminated overburden were removed were surveyed at these times including the limits of exposed bedrock The results of these surveys are shown on Figure 4 The limits of SL-4 site remediation are as follows
Total Site Area Remediated 50860 sf Exposed Ledge 19990 sf
Site Restoration Area 30870 sf
In addition Area 1 is approximately 5416 sf
Note that the total quantity of contaminated overburden and fly ashsoildebris mixture was 6056 tons compared to the estimated 4100 tons from the design studies The primary reasons for the increase include the following
Incorporation of Area 1 from SL-5 in the SL-4 site remediation work
The northern limit of excavation extended further into DA-1 than anticipated in the RA Work Plan
Excavating further west into WA-1 than anticipated in the RA Work Plan
VOC contaminated fly ash and soil in the northwest corner near DAshy1 at a considerable thicknessdepth
The limits of remediation survey are described in the T F Moran letter contained in Appendix B
43 Final As-Built
A final as-built survey was performed by T F Moran on May 21 1996 The results of the survey are shown on Figure 5
TABLE 1 SUMMARY OF ASH REMOVAL
SALEM ACRES SUPERFUND SITE SL-4 AREA
DATE NOMBEraquo0poundLOADS
0AILY TOTAL ifrotfS) i
SEPTS 1 1750
SEPT 1 1 8 13470
SEPT 12 10 21080
SEPT 13 20 45800
SEPT 14 23 50100
SEPT 15 20 43160
SEPT 18 23 46870
SEPT 19 24 54780
SEPT 20 26 52800
SEPT 21 25 47700
SEPT 22 25 46915
SEPT 25 26 51950
SEPT 26 29 56820
SEPT 27 30 55660
SEPT 28 30 58410
SEPT 29 26 53520
OCT2 26 54600
OCT3 26 57000
OCT4 19 41080
OCT5 22 49240
OCT6 26 61860
OCT 10 18 47180
OCT 11 12 33860
OCT 13 17 439 40
OCT 17 3 7600
OCT 19 3 7720
CtnVfOtATIVE TOTAL (TONS)
1750
15220
36300
82100
132200
175360
222230
277010
329810
3775 10
424425
476375
5331 95
5888 55
647265
700785
755385
812385
853465
902705
9645 65
1011745
1045605
1089545
1097145
1104865
TABLE 2 SUMMARY OF CONTAMINATED
OVERBURDEN REMOVAL SALEM ACRES SUPERFUND SITE SL-4 AREA
DATE
on 19 OCT 20
OCT 23
OCT 24
OCT 25
OCT 26
OCT 27
OCT 31
NOV 1
NOV2
NOV 6
NOV 8
NOV 9
NOV 21
NOV 28
DEC 7
NUMBER OF LOADS
14
14
14
13
14
16
18
18
12
4
4
8
8
8
9
2
DAILY TOTAL (TONS)
46121
41649
49314
448 59
46225
48054
62358
56186
491 56
14209
14025
29010
27604
35513
33447
7885
CUMULATIVE TOTAL (TONS)
46121
87770
137084
181943
228168
276222
338580
394766
443922
458131
472156
501166
528770
564283
597730
6056 1 5
- -
--
Oct 17 1995 823PM P02 From LTTS OF Mfl INC PHONE No 617 438 S21S
GRftIN SIZE DISTRIBUTION TEST REPORT C c c e
100 i i ^ i i 7 ^ d bdquo bdquo j laquo ii i A j
bdquo9 bdquo
a 2 - a i
t sh
90 X
N^
B0 raquo m lts
-bull
70 Sk
gtia
Npound G0 shyu
550 gt
UJ bullshy
1u S pound 40 0 ^
30 bull i 20
10
0 2Q 0 1SG 100 10 01 aai 00UL
CRflIM CISC - mm
Test X +3 bull4 GRAVEL bull SflMD bull SILT bull DRY uses LL PI
t 16 00 2Z 3 521 256 SC-SM
SIEVE PERCENT FINCR STEVE PERCENT FINCR Uact on Incrwi nuwtoer ilz ilzi bull flUNSON ST PEABODC
bull bull a 96 3 4 777
15 95 10 714 1 92 e 20 607 Descr pt ion
075 90 40 505 bullSILTY CLAYEY GflNO 0 375 34 50 44 4
100 343
3X1 GRAIN SIZE 200 257
8804D60
gtDia Remarks
xC COEFh 1C1CNT5 UTS OF MASSACHUSETTS INC bull
SS1T to 1 u
Pro jlt-r t No UTS OF naSSACHLKKI lgt IMC Project) CftLCM flCHSCC
5 Richardson Lane
GtoneHam Mft 03 IBB Date 101195 Gamn 1 c- No 44fi1A
Figure 1
From UTS OF Mfl INC PHONE No 517 438 6216 Oct 17 1995 824PM F03
SOT ANALYSIS REPORT FOR NEW LAWN 101195
SOIL AND PLANT TISSUE TESTING LABWEST EXPERIMENT STATIONUNIVERSITY OF MASBACIIUfiFTTr AMHERST MA 01003
LAB NUMBER 3951010-107 BAG NUMBER 23467
DATE BFNT f
SOIL FROM COUNTY SOIL WEIGHT 537 g5cn CROP TURFORASS
UTS OF MASS INC COMMENTS ORGANIC MATTER 6 RICHARDSON LANE STONEHAM MA 02180
SAMPLE ID 4461B
LIMESTONE AND FERTILIZER RECOMMCNDATIONS FOR NEW LAWN CONSTRUCTION
No limestone ia required If peat mooc or similar material ia to be incorporated) see enclosed fact sheet
Fertilizer (per 10OO sq ft) 2 1ba N 2 Ibo P2O5 and O 1 bs KZO
Many fertilizer sources and rates may combine to provide acceptable turfgraes establ iahmont either from seed or aod One or two options baaed on this soil teat follow
Incorporate EITHER a 17-23-6 starter fert111zar at 10 lbs1000 sq ft OR a 30-3-3 lawn fertilizer at 7 1b81000 aq ft plus a 0-45-0 (triple superphosphate) fertilizer at 4 lbs1000 aq ft Hnto the top 3 to 4 inches of soil Retest Bull ona year after turf establishment
PLEASE read the enclosed fact sheets for niora specific Information on fertilization and liming procadurea
SOIL pH 71 NITROGEN NO3-N = Oa ppm NH4-N = 5 ppm BUFFER pH 74 ORGANIC MATTER 72 X (Desirable range 4-10X)
NUTRIENT_LEVELS_PPM_| Low Medium High Very High Phosphorus (P) 8 |XXXXXXXXXXXXX Potaaaium (K) 292 [XXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXX Calcium (Ca) 237S XXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXX Magnesium (Mg) 237 JXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXX
CATION EXCII CAP PERCENT BASE SATURATION MICRONUTRIENT LEVELS 130 Meq100g K= 52 Mg=134 Ca=816 ALL NORMAL
CXTRACTABLE ALUMINUM 41 ppm (Soil ranglaquo 10-250 ppm)
The lead level in thio soil 1s low
COMPUTER PROGRAM5-RECOMMENDATIONRbYOtHIOFPtANT~ampSOILSCI UMASS-AMHERST
Figure 2
TARGET SHEET
THE MATERIAL DESCRIBED BELOW WAS NOT SCANNED BECAUSE
(X) OVERSIZED
() NON-PAPER MEDIA
() OTHER
DESCRIPTION DOC 14732 DRAFT FINAL REMEDIAL CONSTRUCTION REPORT FIGURE 3 TOPOGRAPHIC PLAN SL-4 AREA BOTTOM OF FLY ASH SALEM ACRES SHEET 1 OF 1
THE OMITTED MATERIAL IS AVAILABLE FOR REVIEW BY APPOINTMENT
AT THE EPA NEW ENGLAND SUPERFUND RECORDS CENTER BOSTON MA
TARGET SHEET
THE MATERIAL DESCRIBED BELOW WAS NOT SCANNED BECAUSE
(X) OVERSIZED
() NON-PAPER MEDIA
() OTHER
DESCRIPTION DOC 14732 DRAFT FINAL REMEDIAL CONSTRUCTION REPORT FIGURE 4 TOPOGRAPHIC PLAN SL-4 AREA LIMIT OF REMEDIATION SALEM ACRES SHEET 1OF1
THE OMITTED MATERIAL IS AVAILABLE FOR REVIEW BY APPOINTMENT
AT THE EPA NEW ENGLAND SUPERFUND RECORDS CENTER BOSTON MA
TARGET SHEET
THE MATERIAL DESCRIBED BELOW WAS NOT SCANNED BECAUSE
(X) OVERSIZED
() NON-PAPER MEDIA
() OTHER
DESCRIPTION DOC 14732 DRAFT FINAL REMEDIAL CONSTRUCTION REPORT FIGURE 5 TOPOGRAPHIC PLAN SL-4 AREA AS-BUILT PLAN SALEM ACRES SHEET 1 OF 1
THE OMITTED MATERIAL IS AVAILABLE FOR REVIEW BY APPOINTMENT
AT THE EPA NEW ENGLAND SUPERFUND RECORDS CENTER BOSTON MA
(i)
^mft^m
VIEW OF BARCELONA AVENUE THROUGH ENTRANCE GATE PRECONT RUCTION
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(2)
VIEW OF ACCESS ROAD LOOKING NORTH SL-4 ON LEFT PRECONSTRUCTION
VIEW OF ACCESS ROAD LOOKING NORTH SL-4 ON LEFT DA-1 TO LEFT OF PICKUP TRUCK
PRECONSTRUCTION
(3)
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
O ID a CO z O OHI
CO UJ
OO_l
t CO ii-O
(5)
VIEW OF BOUNDARY BETWEEN SL-4 AND DA-1 LOOKING WEST PRECONSTRUCTION
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(6)
EROSION CONTROLS LOOKING NORTH FROM CORNER OF SL-4SL-5 ADJACENT TO WA-1 PRECONSTRUCTION
(7)
TRUCK LOADING PAD LOOKING NORTHWEST FROM SUPPORT ZONE
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(8)
DECONTAMINATION PAD LOOKING NORTHWEST FROM SUPPORT ZONE
(9)
EXCAVATION OF FLY ASH LOOKING NORTHWEST FROM CRZ NOTE WATER FOR DUST CONTROL
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(10)
VIEW LOOKING WEST AFTER REMOVAL OF FLY ASH NOTE WA-1 BEYOND EROSION CONTROLS
(11)
EXCAVATION OF CONTAMINATED OVERBURDEN LOOKING SOUTH FROM DA-1 BOUNDARY
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(12)
VIEW OF RESTORED SITE LOOKING WEST TOWARD WA-1
0
ltu
wsectbull
D Q
O
O z ^ O O_J LJJ
Q LJJ a o te LJJ
eg 3
(14)
VIEW OF RESTORED SITE LOOKING NORTH TOWARD DA-1 ALONG ACCESS ROAD
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(15)
gtbull bdquobdquo -
VIEW OF RESTORED SITE LOOKING SOUTH TOWARD SL-5
iu O
of bullo
01 u I ltO
w
o B ltabulls to 10
3
I Q Z
O m ^mdash
i sect^^ nu0 (- co^gtW IO - z zilaquo O O 5gl
oLU uj
V) LUo a o LU
(17)
VIEW OF RESTORED SITE ON DA-1 SJDE OF FENCE - LOOKING ST
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(18)
VIEW OF RESTORED SITE ON DA-1 SIDE OF FENCE - LOOKING WEST SL-4 ON RIGHT
APPENDIX A
ANALYTICAL RESULTS FOR
PONDED WATER
110795 1638 copy617 890 3883 TMA-WALTHAM ] 002007
PRELIMINARY REPORT UNAUDITED RESULTS
Thenno Analytical 300 Second Avenue PO Box 521 Waltham HA 02254
Attn Client Services Phone (617) 890-7200
Cashins amp Associates Order S5-11-034 55 Cambridge Street Date 110795 1522 Burlington HA 01803 Work ID Salem Acres Water
Date Received 110295 Attn Bob Cashins Date Completed
Purchase Order NA Invoice Number Client Code CASHINS
SAMPLE IDENTIFICATION
Sample Sample Number Description 01 11019S-924-01A
Sample Number 04
Sample Description
110195-9Z4-01D 02 110195-924-01B 05 110195-924-01E 03 110195-924-01C
Certified By
110795 1638 copy617 890 3883 TMA-WALTHAM 003007
PRELIMINARY REPORT UNAUDITED RESULTS
Order f S5-11-034 Thermo Analytical Page 2 110795 1522 TEST RESULTS BY SAHPLE
Test Description Volatile Organics- Aqueous Method EPA_8240 Test Code Collected 110195 02-00 Category WATER
DATE INJECTED 110695 DILUTION FACTOR 100 All results reported 1n ugL
COMPOUND RESULT DET LIMIT COMPOUND RESULT
Chloromethane U 10 Broroodi chl oromethane U Vinyl Chloride U 10 2-Chloroethyl Vinyl Ether U
Bromxnethane U 10 4-dethyl -2-pentanone U Chloroethane U 10 c1 3-1 3-Di chl oropropene U
Trichlorofluoronwthane U 50 Tol uene U Acetone 17 10 trans-1 3-Di chl oropropene LI
11-Oichloroethene U 50 11 2-Tri chl oroethane J Carbon Dlsulfide U 50 2-Hexanone U
Methyl ene Chloride U 50 Tetrachl oroethene U 12-Oichloroethene (total) U 50 D1 bromochl oromethane U
11-01 Chloroethane U 50 Chlorobenzene U Vinyl Acetate U 10 Ethyl benzene U
2-Butanone U 10 in and p-Xylene U Chloroform U 50 o-Xylene U
111-Tri Chloroethane U 50 Styrene U Carbon Tetrachlortde U 50 Broraoform U
Benzene U 50 112 2-Tat rachl oroethane U 12-01 Chloroethane U 50 1 3-01 chl orobenzene U
Trichloroethene U 50 I 4-Di chl orobenzene U 12-Dichloropropane U 50 12-01 chl orobenzene U
SURROGATE STANDARDS RESULT LEVEL X RECOVERY
12-Dichloroethane-D4 52 50 104 Toluene-08 47 50 94
l-Bromo-4-fluorobenzene 56 50 112
NOTES AND DEFINITIONS FOR THIS REPORT U =bull Undetected at stated detection limit
VOAJI
OET LIMIT
50 50
10 50 50 50 50 10
5 0 50 5 0 5 0 50 50 50 50 50 50 50 50
110795 1639 copy617 890 3883 TMA-WALTHAM copy004007
PRELIMINARY REPORT UNAUDITED RESULTS
Order t S5-11-034 Thermo Analytical Page 4 110795 1522 TEST RESULTS BY SAMPLE
ianple Description 110195-924-010 Lab No 04A Test Description RCRA Metals 1n Water Method SW846 Test Code
Collected 110195 0200 Category WATER
METAL RESULT DETECTION LIMIT METAL RESULT DETECTION LIMIT
Ag Silver U 10 As Arsenic 870 50
Ba Bar inn B69 10 Pb Lead U 50
Cd Cadmium U 50 Se Sel en1 um Z15 50
Cr Chromi um U 20 Hg Mercury U 020
NOTES AND DEFINITIONS FOR THIS REPORT All results reported in ugL U gt Undetected at stated detection limit
110795 1640 Q617 890 3883 TMA-WALTHAM 0005007
PRELIMINARY REPORT UNAUDITED RESULTS
Order S5-11-034 Thermo Analytical Page 5 110795 1522 REGULAR TEST RESULTS BY TEST
Chemical Oxygen Demand Mlnimun Maximum Method EPA600 4101
Sap Sample Description Result Units Limit Prepared Analyzed By 05A 110195-924-01E 64 bullgL 50 110395 110395 JD
Petroleum Hydrocarbons-H20 Minimum Maximum Method EPA600 4181
Samp Sample Description Result Units Limit Prepared Analyzed By 01A 110195-924-01A 108 mgL 050 110395 110395 JO
110795 1640 reg617 890 3883 TMA-WALTHAM copy006007
PRELIMINARY REPORT UNAUDITED RESULTS
Order I S5-11-034 Therm Analytical Page 6 110795 1522 TEST METHODOLOGIES
USEPA Test Methods for Evaluating Solid Wastes (SUS46 Third Edition) Method 7470 - Preparation of water for Mercury analysis
USEPA Test Methods for Evaluating Solid Vastes (SW846 Third Edition) Method 3010 - Add digestion of aqueous samples and extracts for total metals for analysis by Flame Atomic Absorption Spectroscopy or Inductively Coupled Plasma Spectroscopy
USEPA Test Methods for Evaluating Solid Vastes (SWB46 Third Edition Method 8270 mdash Gas ChroroatographyMass Spectrometry for PAHs
Volatile Organics in Water - Hazardous Substance List
SV846 Method 8240 - Modified
Test Methods for Evaluating Solid Waste SU-846 US EPA Office of Solid Waste and Emergency Response Washington 3rd Edition
Aqueous sanples are analyzed in accordance with Method 8240 using a purge and trap technique followed by 64s ChromatographyMass Spectroscopy
Quality assurance procedures for GCMS Include daily tuning and calibration of the mass spectrometer and the use of surrogate standards in each sample to monitor method performance Quantitatton is performed by the Internal standard method Analysis of blanks duplicate samples and standards are run frequently as further quality assurance procedures
USEPA Test Methods for Evaluating Solid Wastes (SW846 Third Edition) Method 3S10 mdash Separatory Funnel Liquid-Liquid Extraction
EPA-6004-79-020 - Chemical Oxygen Demand - Titrimetric Mid-Level Method 4101
EPA6004-79-020 - Petroleum Hydrocarbons 1n Water Total Recoverable Method 4181 (Spectrophotometric Infrared)
110795 1641 copy617 890 3883 TMA-WALTHAM copy007007
APPENDIX B
QUANTITY SURVEY DOCUMENTATION
TFMORAN INC Surveying - Engineering - Land Planning SoilsWetlands Mapping - Landscape Architecture
January 15 1996
Mr Jack Enos Vice President TFord Company Inc 118 Tenney Street Georgetown MA 01833
RE Survey Results - Salem Acres - SL4 Area Salem Massachusetts
Dear Jack
This letter amends the letter of December 13 1995 per our review last week
TFMoran Inc performed topographic surveys at the Salem Acres site on April 21 1994 for GEI Consultants prior to removal of material and for TFord Company on October 18 1995 after the removal of material The survey data from the original survey in 1994 was adjusted thirty feet higher to correct for a datum difference from current site datum This was due to the original reporting of the Site Benchmark (TP34) elevation as 11464 rather than 14464 which is the correct elevation
Once both topographic surfaces were on the site datum the raw cut volume was obtained by Eaglepoint (Volumes Module) Software utilizing the prismoidal method comparing the two surfaces For reference please see the attached topographic plan which superimposes the October 15 1995 contours (dark lines) over the April 21 1994 contours The volume is based on the intersection of the two surfaces Also it was noted that stock piles of material did exist on site which were not surveyed at the time
The final raw cut volume arrived at by the above methods is 12749 Cubic Yards
In November and December of 1995 the site was resurveyed to locate the area of exposed ledge at the site The results of this survey are shown on the attached topographic worksheet dated November 3 1995 and last revised January 15 1996 The results of the survey indicate the total site area to be 50860 sq ft or 117 acres The total area of exposed ledge surveyed is 19990 sq ft or 46 acres If you have any questions regarding the above call me directly Thank you
Sincerely
John W Myhaver Jr ^_ Field Operations Manager
Enclosure ItorLltr
Route 101 Bedford NH 03110 Phone (603) 472-4488 FAX (603) 472-9747
APPENDIX C
HEALTH AND SAFETY PHASE-OUT REPORT
HEALTH AND SAFETY PHASE-OUT REPORT SALEM ACRES SL-4 AREA
Introduction
During remediation work on SL-4 Health and Safety Monitoring was performed Cashins amp Associates Inc of Reading MA performed the following work as a subcontractor to TFCI
1) Preparation of a site-specific Health and Safety Plan (dated September 1 1995)
2) Provide a Field TechnicianIndustrial Hygienist to serve as Site Safety and Health Officer (SSHO) and to conduct air and noise monitoring
3) Provide a Certified Industrial Hygienist to review Health and Safety and to conduct site specific training (record of training included at end of Appendix C)
4) Collect 8-hour air samples for worker exposure and ambient air at the Barcelona Avenue gate Arrange for analysis of the samples and report results
5) Prepare daily and weekly Health and Safety reports
6) Prepare a Health and Safety Phase-Out Report
In general the following health and safety practices were followed
1) All workers wore hard hats safety glasses work boots gloves and hearing protection as minimum level PPE
2) When working in the exclusion zone workers wore in addition to above tyvek rubber overboots and rubber coated gloves When dust was a potential concern an industrial grade dustmist mask was also worn This level of PPE was considered Level D modified
3) Workers leaving the exclusion zone removed PPE (tyveks gloves boots and masks) in the support zone and either disposed of the items or decontaminated them
4) Workers andor visitors without 40-hour OSHA training were not permitted to enter the exclusion zone
Attached is a report prepared by Cashins amp Associates along with weekly Health and Safety Summary Reports prepared by the Field Hygienist In summary the air monitoring results indicate no levels exceeding the applicable exposure guidelines except one instance
During excavation of contaminated overburden in the northwest comer of the site an area of VOC contaminated soil was encountered Total VOCs levels measured using a PID exceeded the action level established in the Health and Safety Plan The SSHO advised TFCI to upgrade to Level C PPE in order to backfill the excavation in this area TFCI equipment operator upgraded and backfilled the area The SSHO in consultation with the Cashins CIH advised TFCI to avoid work in this area until the contaminants were characterized GEI sampled the material for waste characterization analysis and provided the results to TFCI Based on the results an action level was established by the CIH for the specific contaminants found Further PID measurements indicated levels below the new action level and work was resumed
The noise monitoring indicated that the noise level at the Barcelona Avenue gate was not exceeded Only one instance of excess noise level in the work zone was recorded (10 db(a) above the ambient noise level or 85 db(a)) Workers wore hearing protection in this instance
mdash 07171996 1601 6179444032 CASHIMS S ASSOCIATES PAGE 02
CASHINS amp Associates Inc
ItxhalrM Hy-gifnr A Invtronmtnltl Tttling
July 17 1996
Mr Jack Enos T Ford Company Inc USTenney Street Georgetown MA 01833
Dear Jack
The Site Safety and Health Officer (SSHO) from Cashing amp Associates Inc performed daily inspections of the SL-4 area Salem Acres Superfund Site between 9595 and 12195 in accordance with the Health amp Safety Plan (HSP) for the site Daily inspection logs were submitted every day No accidentsincidents were reported during the work period
In accordance with the Health amp Safety Plan the SSHO performed daily air and noise monitoring at the site during Ac project Samples were collected for metals (lead beryllium chromium arsenic) and Polynuclear Aromatic Hydrocarbons (PAHs) at the site perimeter and for workers exposure determination Coal Tar Pitch Volatiles (a benzene soluble extractables) were also used to determine the workers exposure to PAH compounds Coal Tar Pitch Volatiles (CTPV) were analyzed using OSHA 58 Method If CTPV levels oq personal samples exceed the site criteria of 02 ragm3 the sample was submitted for PAHs analysis All air samples on the site perimeter were analyzed for PAH compounds
Site monitoring air sample collection and results report were done under the supervision of a Certified Industrial Hygienist
Full shift personal worker exposure samples were collected once a week Ambient air samples were collected at the Barcelona Avenue gate about 20 feet to the west of the site gate to determine if site contaminants were migrating off site The ambient air samples were also collected once a week during the project except on rainy days and days without work with contaminated soil
All air samples were analyzed by the American Industrial Hygiene Association accredited ESA Laboratories Inc using the following methods PAHs - NIOSH 5515 Lead - NIOSH 7082 Beryllium - NIOSH 7102 Chromium - NIOSH 7024 Arsenic - NIOSH 7900 Coal Tar Pitch Volatiles - OSHA 58 All methods used are accepted by the industrial hygiene community for 8-hour exposure assessment EPA methods are usually used for ambient air measurements
CRErORTTFOmiOO
80 Mam Street bull Reading MA 01867 bull Phone- 61 7-944-4060 bull Fax 61 7-944-4082
07171996 1601 6179444032 CASHIMS amp ASSOCIATES PAGE 03
The results of air samples for metals and PAHs are presented in Table No 1
All concentrations of metals and PAHs at the site perimeter (Barcelona Avenue) and active work zones were below the OSHA Permissible Exposure Limits (PEL) and the American Conference of Governmental Industrial Hygicnists Threshold Limit Value (ACGIH TLV) Two personal samples collected on October 19 and October 23rd showed Coal Tar Pitch Volatiles (CTPV) results above OSHA PEL and AIHA TLV limits Both samples were resubmittcd to the lab for further analysis to determine if PAH compounds are present because the CTPV results were above site criteria
The results of the PAH concentrations for the personal sample on Mark Goodwin on October 19 1995 during excavation and washing trucks and for the personal sample on Ron Maker on October 23 1995 during excavating and cleaning rocks by compressed air were below OSHA PEL and ACGIH TLV limits
The SSHO performed noise monitoring according to the HSP at the exclusion zone and at the Barcelona Avenue site perimeter fence A Dupont sound level meter was used for noise monitoring The noise level in the exclusion zone during all operations except one did not exceed the on site criteria of 85 dB(a) During a short time when the air compressor had been used to clean rocks the sound level in the exclusion zone next to the air compressor did exceed 85 dB(a) Ear protection devices were worn by the workers during that operation At no time did the noise level at the Barcelona Avenue site perimeter exceed 10 dB(a) above the ambient noise level or 85 dB(a)
The SSHO performed total dust monitoring on a daily basis during the project at the site perimeter downwind of work location and at the site gate using a Miniram real time dust meter The summary of dust monitoring is presented in Table No 2 Total dust concentrations on site and off site did not exceed site criteria of 1 mgm3 and the action level of 05 nigny1
The summary of air monitoring for Volatile Organic Compounds (VOC) is presented in Table No 3 VOC concentrations in the working area did not exceed the on site criteria of 5 ppm in a breathing zone VOC concentrations on the site perimeter did not exceed real time off site criteria of 2 ppm
Five detail reports with results of air sampling were submitted during the project period
Sincerely Cashins amp Associates Inc
Evelina Vaughan Industrial Hygieflfst
CASHINS amp ASSOCIATES Inc
80 Mam Street bull Reading MA 01867 bull Phone61 7-944-4060 bull Fax 617-944-4082
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Ifxtuitral Hygltne A fnvironmtnltt Tuning
W3SXLY HBALTH amp SAFETY PLAN COMPLIANCE SUMMARY R3PORT
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LOCATION gal era Acres Sx^perfund Site 8L-4 Area
DATES INCLUDED IN SUMMARY
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LOCATION Salen Acres Suoerfund Site SL-4 Area
DATES INCLUDED IN SUMMARY
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Industrial Hygitnf amp CmimnmenUl Tinting
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Compan
LOCATION Salem Acres Superfund Site SL-4 Area
DATES INCLUDED IN SUMMARY
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WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Company
LOCATION Salem Acres Superfund Site SL-4 Area
DATES INCLUDED IN SUMMARY J_
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SUMMARIZED BY FOR CASHINS amp ASSOCIATES INC
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CASHINS amp Associates Inc
Industrial Hygifnr amp [nvironmenljl res
SERIOUS HAZARD NOTIFICATION
ISSUED TO REPRESENTING
ISSUED BY REPRESENTING CASHINS S ASSOCIATES INcT DAY DATE ISSUED O04Xmdash 1 bull-bullmdashbull f P^JT
PROJECT NAME_ SITE LOCATION
THE PURPOSE OF THE FOLLOWING STATEMENT IS TO DOCUMENT THE EXISTENCE OF A CONDITION OR CONCERN WHICH CASHINS amp ASSOCIATES INC BELIEVES WARRANTS IMMEDIATE CORRECTIVE ACTION POSSIBLE SOLUTIONS AND OR CORRECTIVE ACTIONS WILL BE INCLUDED IN THIS NOTIFICATION WHEN POSSIBLE THIS NOTIFICATION IS LIMITED TO SITUATIONS THAT REPRESENT EITHER IMMEDIATE DANGER TO LIFE OR HEALTH CONDITIONS OR PREVIOUSLY IDENTIFIED CHRONIC PROBLEMS THAT UNDERMINE OUR ABILITY TO EFFECTIVELY INSURE COMPLIANCE WITH THE REQUIREMENTS OF THE HEALTH AND SAFETY PLAN
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ACKNOWLEDGEMENT OF RECEIPT OF NOTIFICATION NAMECOMPANY DATE
ACKNOWLEDGEMENT OF ISSUANCE OF NOTIFICATION - NAMECOMPANY ^gt j^f^u^^ CASHINS amp ASSOCINC DATE0 IS
55 CAMBRIDGE STREET bull SUITE 201 bull BURLINGTON MA 01 803 bull TEL 61 7-273-9080 bull FAX fgtl 7-273-9084
CISHINS amp Associates Inc
Industrial Hygirne amp Cmimnmtntal Testing
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Company
LOCATION Salem Acres Superfund Site SL-4 Area
DATES INCLUDED IN SUMMARY T
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SUMMARIZED BY FOR CASHINS amp ASSOCIATES INC
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87161996 1650 6179444882 CASHINS amp ASSOCIATES
CASHINSamp Associates Inc
WEEKLY HEALTH amp SA7STT PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Coqpanv
LOCATION Sa^am Acras Super fund 5 jte SL-4 Area
DATES INCLUDED IN SUMMARY bull
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LOCATION Salem Acraa Suoerfund Sita 5L-4
DATES INCLUDED IN SUMMARY bull
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07161996 1650 617944408 CASHING 3 ASSOCIATES PAGE 05
CASHINSamp Associates Inc
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WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT t T Ford Coimbanv
LOCATION t Salam Acraa Suoarfund Site SL-4 Arlaquoa
DATES INCLUDED IN SUMMARYj pound mdashiffofrshy f
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SUMMARIZ2D BY _ ampampS FOR CASHINS amp ASSOCIATES INC
55 CAMBRIDGE STREET bull SUITE 201 bull BURLINGTON MA 01803 lt TEL 617-273-9080 bull FAX 617-273-9084
CASHIMS amp ASSOCIATES PAGE 04 07161996 1658 6179444032
OVSHINSamp Associates Inc
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Company T
LOCATION Salem AcrM Suoerfund Stta 8L-4 Araa
DATES INCLUDED IN SUMMARY
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SUMMARIZED BY pound FOR CASHINS amp ASSOCIATES INC
55 CAMBRIDGE STREET bull SUITE 201 bull BURUNGTON MA 01803 bull TEL 617-273-9080 bull FAX 617-273-9084
07161996 1658 6179444082 CASHIMS 3 ASSOCIATES PAGE 03
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DATES INCLUDED IN SUMMARY
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07151996 18 fO 6179444082 CASHINS S ASSOCIATES PAGE 02
CASHINS amp Associates Inc
WBBKLY HEALTH amp SAFETY FLAK COMPLIANCE SUMMARY REPORT
CLIENT T Ford Compapv
LOCATION i Sal am Acrlaquolaquo Suparfund Sita SL-4 Area
DATES INCLUDED IN SUMMARY i bull pound7 mdash
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SXWMARIZ2D BY FOR CASHINS amp ASSOCIATES INC (
55 CAMBRIDGE STREET SUITE 201 bull SURtlNCTON MA 01803 TEL 617-273-9080 bull FAX 61 7-273-9084
- barcode 14732
- barcodetext SEMS Doc ID 14732
![Page 8: SALEM ACRES SUPERFUND SITE SALEM, MA ...The truck loading pa d consisted of a crushed stone are sea t up along the east sid e o f SL-4 adjacent to the access road A. row of concrete](https://reader036.vdocuments.us/reader036/viewer/2022070114/60729b840fec4e6b4d136a16/html5/thumbnails/8.jpg)
the Access Road Southern - Defined by SL-5 Area except for Area 1 which was
incorporated into SL-4 site remediation work Western - Defined by WA-1 Area
The bottom of excavation was sampled for confirmatory analysis by GEL The results of this analysis are described in the Demonstration of Compliance Report
Table 2 summarizes the daily quantities of contaminated overburden loaded Approximately the same daily quantity was excavated No significant stockpiles of contaminated overburden were maintained
Where bedrock was encountered contaminated soils were scraped off with the excavator The remaining material was removed as part of bedrock cleaning (see Sec 27) A number of boulders were encountered in the overburden MEC elected to have TFCI decontaminate the boulders on the decontamination pad and then incorporated them into the random fill
26 Ponded Water
Removal of fly ash and contaminated overburden along the western side of SL-4 resulted in a low area which collected both surface water run-off and groundwater seepage This area became a temporary pond containing approximately 100000 to 150000 gallons of water The level fluctuated with the level of the adjoining wetlands
In order to discharge the ponded water to the wetlands (WA-1) the discharge would have to meet Federal drinking water quality standards TFCI arranged for sampling and testing of the ponded water The results are contained in Appendix A Although the water met requirements of USEPA and MADEP for chemical contaminants the water was quite turbid and no practical means of removing suspended solids was available
A request was made to SESD to dispose of the ponded water at its Salem Treatment Facility SESD approved this request on November 20 1995
The ponded water was pumped into conventional septage hauling vehicles on November 27 through 30 1995 A total of 125000 gallons was transported to SESD for disposal Random fill was placed in the low area immediately following pumping of ponded water to avoid collection of additional water
27 Bedrock Cleaning
As required by the Specifications all exposed bedrock was cleaned of all fly ash and
contaminated overburden Several techniques andor methods were used to clean bedrock including
a) Manual broom and shovel work b) Compressor with air gun to loosen material from crevices with water
used for dust control c) A Vac-All truck using water andor compressed air to loosen
material d) A broom attached to the bucket of an excavator
The surface of exposed bedrock was generally quite irregular and required considerable effort to remove soil and fly ash from cracks and crevices In some areas the rock is highly weathered and can be removed In these areas a determination was made in conjunction with GEI as to when to stop removal of weathered bedrock
During placement of random fill and loam some areas of exposed bedrock became re-covered with these earth materials TFCI proposed to topsoil and seed on these areas rather than re-cleaning the bedrock GEI EPA and MEC accepted this proposal
3 SITE RESTORATION
31 Random Fill
Random fill for the site restoration was obtained from a borrow pit located on Munson Street in Peabody MA GEI conducted confirmatory sampling of the borrow source The results are contained in the Demonstration of Compliance Report A grain size analysis is provided in Figure 1 A total of 1176 cy of random fill was delivered to the site and spread over all exposed soil subgrade areas The thickness is 6 inches except along the west side of the site where it ranges up to 5 ft thick where contaminated soil and fly ash were encountered at a deeper level (See Sec 4)
The random fill was spread and compacted using a CAT D4H dozer
32 Loam and Seeding
In the Spring of 1996 after Winter shutdown TFCI placed and spread a 6-inch layer of loam The loam was obtained from a loam stockpile located at a new residential subdivision in Ayer MA called Bennetts Brook and furnished to the site by D amp H Loam Company A total of 695 cy of loam was delivered to the site GEI conducted confirmatory sampling of the loam source The results are contained in the Demonstration of Compliance Report A topsoil analysis report is provided as
Figure 2
The loam was spread using a CAT D4H dozer Areas of the slope where the grade was steeper than 4HIV were first hand-seeded and then covered with Erosion Control and Revegetation Mat (ECRM) The entire loamed area was then hydro-seeded on May 14 1996 The seed used is Massachusetts Highway Department Specification M6030 Slope and Shoulder Mix
33 FencingDemobilization
In order to remove fly ash andor contaminated overburden which extended onto DA-1 it was necessary to remove the fence along the south side of DA-1 After completion of remediation work the fence was replaced Because of the winter shutdown TFCI reinstalled the fence prior to site restoration work to secure the DAshy1 area
Following placement of the random fill TFCI demobilized for winter shutdown Due to an early snowfall it was impossible to loam and seed the site prior to winter shutdown TFCI demobilized equipment and support facilities December 8-13 1995
In the Spring of 1996 it was only necessary to mobilize a dozer and small excavator to place and spread loam
4 QUANTITY SURVEYS AND AS-BUILT PLANS
41 Fly Ash Quantity Survey
In order to calculate the insitu quantity of fly ash for payment TFCI engaged a subcontractor T F Moran for survey work and quantity estimates T F Moran performed an existing conditions topographic survey on April 21 1994 for design studies conducted by GEI Consultants Inc This survey was updated and verified on September 8 1995 by T F Moran for TFCI In addition a stockpile of fly ash removed from SL-5 was also surveyed on this date
T F Moran surveyed the bottom of fly ash on October 18 1995 The results of the fly ash quantity surveys are shown on Figure 3 The quantities of fly ash are as follows
SL-4 Fly Ash 12750 cy SL-5 Fly Ash (stockpiled on SL-4) 520 cv
13270 cy
In addition there was an estimated 1500 cy of fly ash not included in the TF
Moran surveys because the material was in or under active stockpiles at the time of the survey The quantity survey and method of calculation is described in a letter from T F Moran dated January 15 1996 and contained in Appendix B
42 Limits of Remediation
In order to document the limits of remediation T F Moran surveyed the site on November 1 and December 5 1995 Areas where contaminated overburden were removed were surveyed at these times including the limits of exposed bedrock The results of these surveys are shown on Figure 4 The limits of SL-4 site remediation are as follows
Total Site Area Remediated 50860 sf Exposed Ledge 19990 sf
Site Restoration Area 30870 sf
In addition Area 1 is approximately 5416 sf
Note that the total quantity of contaminated overburden and fly ashsoildebris mixture was 6056 tons compared to the estimated 4100 tons from the design studies The primary reasons for the increase include the following
Incorporation of Area 1 from SL-5 in the SL-4 site remediation work
The northern limit of excavation extended further into DA-1 than anticipated in the RA Work Plan
Excavating further west into WA-1 than anticipated in the RA Work Plan
VOC contaminated fly ash and soil in the northwest corner near DAshy1 at a considerable thicknessdepth
The limits of remediation survey are described in the T F Moran letter contained in Appendix B
43 Final As-Built
A final as-built survey was performed by T F Moran on May 21 1996 The results of the survey are shown on Figure 5
TABLE 1 SUMMARY OF ASH REMOVAL
SALEM ACRES SUPERFUND SITE SL-4 AREA
DATE NOMBEraquo0poundLOADS
0AILY TOTAL ifrotfS) i
SEPTS 1 1750
SEPT 1 1 8 13470
SEPT 12 10 21080
SEPT 13 20 45800
SEPT 14 23 50100
SEPT 15 20 43160
SEPT 18 23 46870
SEPT 19 24 54780
SEPT 20 26 52800
SEPT 21 25 47700
SEPT 22 25 46915
SEPT 25 26 51950
SEPT 26 29 56820
SEPT 27 30 55660
SEPT 28 30 58410
SEPT 29 26 53520
OCT2 26 54600
OCT3 26 57000
OCT4 19 41080
OCT5 22 49240
OCT6 26 61860
OCT 10 18 47180
OCT 11 12 33860
OCT 13 17 439 40
OCT 17 3 7600
OCT 19 3 7720
CtnVfOtATIVE TOTAL (TONS)
1750
15220
36300
82100
132200
175360
222230
277010
329810
3775 10
424425
476375
5331 95
5888 55
647265
700785
755385
812385
853465
902705
9645 65
1011745
1045605
1089545
1097145
1104865
TABLE 2 SUMMARY OF CONTAMINATED
OVERBURDEN REMOVAL SALEM ACRES SUPERFUND SITE SL-4 AREA
DATE
on 19 OCT 20
OCT 23
OCT 24
OCT 25
OCT 26
OCT 27
OCT 31
NOV 1
NOV2
NOV 6
NOV 8
NOV 9
NOV 21
NOV 28
DEC 7
NUMBER OF LOADS
14
14
14
13
14
16
18
18
12
4
4
8
8
8
9
2
DAILY TOTAL (TONS)
46121
41649
49314
448 59
46225
48054
62358
56186
491 56
14209
14025
29010
27604
35513
33447
7885
CUMULATIVE TOTAL (TONS)
46121
87770
137084
181943
228168
276222
338580
394766
443922
458131
472156
501166
528770
564283
597730
6056 1 5
- -
--
Oct 17 1995 823PM P02 From LTTS OF Mfl INC PHONE No 617 438 S21S
GRftIN SIZE DISTRIBUTION TEST REPORT C c c e
100 i i ^ i i 7 ^ d bdquo bdquo j laquo ii i A j
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90 X
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550 gt
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10
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CRflIM CISC - mm
Test X +3 bull4 GRAVEL bull SflMD bull SILT bull DRY uses LL PI
t 16 00 2Z 3 521 256 SC-SM
SIEVE PERCENT FINCR STEVE PERCENT FINCR Uact on Incrwi nuwtoer ilz ilzi bull flUNSON ST PEABODC
bull bull a 96 3 4 777
15 95 10 714 1 92 e 20 607 Descr pt ion
075 90 40 505 bullSILTY CLAYEY GflNO 0 375 34 50 44 4
100 343
3X1 GRAIN SIZE 200 257
8804D60
gtDia Remarks
xC COEFh 1C1CNT5 UTS OF MASSACHUSETTS INC bull
SS1T to 1 u
Pro jlt-r t No UTS OF naSSACHLKKI lgt IMC Project) CftLCM flCHSCC
5 Richardson Lane
GtoneHam Mft 03 IBB Date 101195 Gamn 1 c- No 44fi1A
Figure 1
From UTS OF Mfl INC PHONE No 517 438 6216 Oct 17 1995 824PM F03
SOT ANALYSIS REPORT FOR NEW LAWN 101195
SOIL AND PLANT TISSUE TESTING LABWEST EXPERIMENT STATIONUNIVERSITY OF MASBACIIUfiFTTr AMHERST MA 01003
LAB NUMBER 3951010-107 BAG NUMBER 23467
DATE BFNT f
SOIL FROM COUNTY SOIL WEIGHT 537 g5cn CROP TURFORASS
UTS OF MASS INC COMMENTS ORGANIC MATTER 6 RICHARDSON LANE STONEHAM MA 02180
SAMPLE ID 4461B
LIMESTONE AND FERTILIZER RECOMMCNDATIONS FOR NEW LAWN CONSTRUCTION
No limestone ia required If peat mooc or similar material ia to be incorporated) see enclosed fact sheet
Fertilizer (per 10OO sq ft) 2 1ba N 2 Ibo P2O5 and O 1 bs KZO
Many fertilizer sources and rates may combine to provide acceptable turfgraes establ iahmont either from seed or aod One or two options baaed on this soil teat follow
Incorporate EITHER a 17-23-6 starter fert111zar at 10 lbs1000 sq ft OR a 30-3-3 lawn fertilizer at 7 1b81000 aq ft plus a 0-45-0 (triple superphosphate) fertilizer at 4 lbs1000 aq ft Hnto the top 3 to 4 inches of soil Retest Bull ona year after turf establishment
PLEASE read the enclosed fact sheets for niora specific Information on fertilization and liming procadurea
SOIL pH 71 NITROGEN NO3-N = Oa ppm NH4-N = 5 ppm BUFFER pH 74 ORGANIC MATTER 72 X (Desirable range 4-10X)
NUTRIENT_LEVELS_PPM_| Low Medium High Very High Phosphorus (P) 8 |XXXXXXXXXXXXX Potaaaium (K) 292 [XXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXX Calcium (Ca) 237S XXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXX Magnesium (Mg) 237 JXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXX
CATION EXCII CAP PERCENT BASE SATURATION MICRONUTRIENT LEVELS 130 Meq100g K= 52 Mg=134 Ca=816 ALL NORMAL
CXTRACTABLE ALUMINUM 41 ppm (Soil ranglaquo 10-250 ppm)
The lead level in thio soil 1s low
COMPUTER PROGRAM5-RECOMMENDATIONRbYOtHIOFPtANT~ampSOILSCI UMASS-AMHERST
Figure 2
TARGET SHEET
THE MATERIAL DESCRIBED BELOW WAS NOT SCANNED BECAUSE
(X) OVERSIZED
() NON-PAPER MEDIA
() OTHER
DESCRIPTION DOC 14732 DRAFT FINAL REMEDIAL CONSTRUCTION REPORT FIGURE 3 TOPOGRAPHIC PLAN SL-4 AREA BOTTOM OF FLY ASH SALEM ACRES SHEET 1 OF 1
THE OMITTED MATERIAL IS AVAILABLE FOR REVIEW BY APPOINTMENT
AT THE EPA NEW ENGLAND SUPERFUND RECORDS CENTER BOSTON MA
TARGET SHEET
THE MATERIAL DESCRIBED BELOW WAS NOT SCANNED BECAUSE
(X) OVERSIZED
() NON-PAPER MEDIA
() OTHER
DESCRIPTION DOC 14732 DRAFT FINAL REMEDIAL CONSTRUCTION REPORT FIGURE 4 TOPOGRAPHIC PLAN SL-4 AREA LIMIT OF REMEDIATION SALEM ACRES SHEET 1OF1
THE OMITTED MATERIAL IS AVAILABLE FOR REVIEW BY APPOINTMENT
AT THE EPA NEW ENGLAND SUPERFUND RECORDS CENTER BOSTON MA
TARGET SHEET
THE MATERIAL DESCRIBED BELOW WAS NOT SCANNED BECAUSE
(X) OVERSIZED
() NON-PAPER MEDIA
() OTHER
DESCRIPTION DOC 14732 DRAFT FINAL REMEDIAL CONSTRUCTION REPORT FIGURE 5 TOPOGRAPHIC PLAN SL-4 AREA AS-BUILT PLAN SALEM ACRES SHEET 1 OF 1
THE OMITTED MATERIAL IS AVAILABLE FOR REVIEW BY APPOINTMENT
AT THE EPA NEW ENGLAND SUPERFUND RECORDS CENTER BOSTON MA
(i)
^mft^m
VIEW OF BARCELONA AVENUE THROUGH ENTRANCE GATE PRECONT RUCTION
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(2)
VIEW OF ACCESS ROAD LOOKING NORTH SL-4 ON LEFT PRECONSTRUCTION
VIEW OF ACCESS ROAD LOOKING NORTH SL-4 ON LEFT DA-1 TO LEFT OF PICKUP TRUCK
PRECONSTRUCTION
(3)
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
O ID a CO z O OHI
CO UJ
OO_l
t CO ii-O
(5)
VIEW OF BOUNDARY BETWEEN SL-4 AND DA-1 LOOKING WEST PRECONSTRUCTION
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(6)
EROSION CONTROLS LOOKING NORTH FROM CORNER OF SL-4SL-5 ADJACENT TO WA-1 PRECONSTRUCTION
(7)
TRUCK LOADING PAD LOOKING NORTHWEST FROM SUPPORT ZONE
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(8)
DECONTAMINATION PAD LOOKING NORTHWEST FROM SUPPORT ZONE
(9)
EXCAVATION OF FLY ASH LOOKING NORTHWEST FROM CRZ NOTE WATER FOR DUST CONTROL
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(10)
VIEW LOOKING WEST AFTER REMOVAL OF FLY ASH NOTE WA-1 BEYOND EROSION CONTROLS
(11)
EXCAVATION OF CONTAMINATED OVERBURDEN LOOKING SOUTH FROM DA-1 BOUNDARY
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(12)
VIEW OF RESTORED SITE LOOKING WEST TOWARD WA-1
0
ltu
wsectbull
D Q
O
O z ^ O O_J LJJ
Q LJJ a o te LJJ
eg 3
(14)
VIEW OF RESTORED SITE LOOKING NORTH TOWARD DA-1 ALONG ACCESS ROAD
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(15)
gtbull bdquobdquo -
VIEW OF RESTORED SITE LOOKING SOUTH TOWARD SL-5
iu O
of bullo
01 u I ltO
w
o B ltabulls to 10
3
I Q Z
O m ^mdash
i sect^^ nu0 (- co^gtW IO - z zilaquo O O 5gl
oLU uj
V) LUo a o LU
(17)
VIEW OF RESTORED SITE ON DA-1 SJDE OF FENCE - LOOKING ST
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(18)
VIEW OF RESTORED SITE ON DA-1 SIDE OF FENCE - LOOKING WEST SL-4 ON RIGHT
APPENDIX A
ANALYTICAL RESULTS FOR
PONDED WATER
110795 1638 copy617 890 3883 TMA-WALTHAM ] 002007
PRELIMINARY REPORT UNAUDITED RESULTS
Thenno Analytical 300 Second Avenue PO Box 521 Waltham HA 02254
Attn Client Services Phone (617) 890-7200
Cashins amp Associates Order S5-11-034 55 Cambridge Street Date 110795 1522 Burlington HA 01803 Work ID Salem Acres Water
Date Received 110295 Attn Bob Cashins Date Completed
Purchase Order NA Invoice Number Client Code CASHINS
SAMPLE IDENTIFICATION
Sample Sample Number Description 01 11019S-924-01A
Sample Number 04
Sample Description
110195-9Z4-01D 02 110195-924-01B 05 110195-924-01E 03 110195-924-01C
Certified By
110795 1638 copy617 890 3883 TMA-WALTHAM 003007
PRELIMINARY REPORT UNAUDITED RESULTS
Order f S5-11-034 Thermo Analytical Page 2 110795 1522 TEST RESULTS BY SAHPLE
Test Description Volatile Organics- Aqueous Method EPA_8240 Test Code Collected 110195 02-00 Category WATER
DATE INJECTED 110695 DILUTION FACTOR 100 All results reported 1n ugL
COMPOUND RESULT DET LIMIT COMPOUND RESULT
Chloromethane U 10 Broroodi chl oromethane U Vinyl Chloride U 10 2-Chloroethyl Vinyl Ether U
Bromxnethane U 10 4-dethyl -2-pentanone U Chloroethane U 10 c1 3-1 3-Di chl oropropene U
Trichlorofluoronwthane U 50 Tol uene U Acetone 17 10 trans-1 3-Di chl oropropene LI
11-Oichloroethene U 50 11 2-Tri chl oroethane J Carbon Dlsulfide U 50 2-Hexanone U
Methyl ene Chloride U 50 Tetrachl oroethene U 12-Oichloroethene (total) U 50 D1 bromochl oromethane U
11-01 Chloroethane U 50 Chlorobenzene U Vinyl Acetate U 10 Ethyl benzene U
2-Butanone U 10 in and p-Xylene U Chloroform U 50 o-Xylene U
111-Tri Chloroethane U 50 Styrene U Carbon Tetrachlortde U 50 Broraoform U
Benzene U 50 112 2-Tat rachl oroethane U 12-01 Chloroethane U 50 1 3-01 chl orobenzene U
Trichloroethene U 50 I 4-Di chl orobenzene U 12-Dichloropropane U 50 12-01 chl orobenzene U
SURROGATE STANDARDS RESULT LEVEL X RECOVERY
12-Dichloroethane-D4 52 50 104 Toluene-08 47 50 94
l-Bromo-4-fluorobenzene 56 50 112
NOTES AND DEFINITIONS FOR THIS REPORT U =bull Undetected at stated detection limit
VOAJI
OET LIMIT
50 50
10 50 50 50 50 10
5 0 50 5 0 5 0 50 50 50 50 50 50 50 50
110795 1639 copy617 890 3883 TMA-WALTHAM copy004007
PRELIMINARY REPORT UNAUDITED RESULTS
Order t S5-11-034 Thermo Analytical Page 4 110795 1522 TEST RESULTS BY SAMPLE
ianple Description 110195-924-010 Lab No 04A Test Description RCRA Metals 1n Water Method SW846 Test Code
Collected 110195 0200 Category WATER
METAL RESULT DETECTION LIMIT METAL RESULT DETECTION LIMIT
Ag Silver U 10 As Arsenic 870 50
Ba Bar inn B69 10 Pb Lead U 50
Cd Cadmium U 50 Se Sel en1 um Z15 50
Cr Chromi um U 20 Hg Mercury U 020
NOTES AND DEFINITIONS FOR THIS REPORT All results reported in ugL U gt Undetected at stated detection limit
110795 1640 Q617 890 3883 TMA-WALTHAM 0005007
PRELIMINARY REPORT UNAUDITED RESULTS
Order S5-11-034 Thermo Analytical Page 5 110795 1522 REGULAR TEST RESULTS BY TEST
Chemical Oxygen Demand Mlnimun Maximum Method EPA600 4101
Sap Sample Description Result Units Limit Prepared Analyzed By 05A 110195-924-01E 64 bullgL 50 110395 110395 JD
Petroleum Hydrocarbons-H20 Minimum Maximum Method EPA600 4181
Samp Sample Description Result Units Limit Prepared Analyzed By 01A 110195-924-01A 108 mgL 050 110395 110395 JO
110795 1640 reg617 890 3883 TMA-WALTHAM copy006007
PRELIMINARY REPORT UNAUDITED RESULTS
Order I S5-11-034 Therm Analytical Page 6 110795 1522 TEST METHODOLOGIES
USEPA Test Methods for Evaluating Solid Wastes (SUS46 Third Edition) Method 7470 - Preparation of water for Mercury analysis
USEPA Test Methods for Evaluating Solid Vastes (SW846 Third Edition) Method 3010 - Add digestion of aqueous samples and extracts for total metals for analysis by Flame Atomic Absorption Spectroscopy or Inductively Coupled Plasma Spectroscopy
USEPA Test Methods for Evaluating Solid Vastes (SWB46 Third Edition Method 8270 mdash Gas ChroroatographyMass Spectrometry for PAHs
Volatile Organics in Water - Hazardous Substance List
SV846 Method 8240 - Modified
Test Methods for Evaluating Solid Waste SU-846 US EPA Office of Solid Waste and Emergency Response Washington 3rd Edition
Aqueous sanples are analyzed in accordance with Method 8240 using a purge and trap technique followed by 64s ChromatographyMass Spectroscopy
Quality assurance procedures for GCMS Include daily tuning and calibration of the mass spectrometer and the use of surrogate standards in each sample to monitor method performance Quantitatton is performed by the Internal standard method Analysis of blanks duplicate samples and standards are run frequently as further quality assurance procedures
USEPA Test Methods for Evaluating Solid Wastes (SW846 Third Edition) Method 3S10 mdash Separatory Funnel Liquid-Liquid Extraction
EPA-6004-79-020 - Chemical Oxygen Demand - Titrimetric Mid-Level Method 4101
EPA6004-79-020 - Petroleum Hydrocarbons 1n Water Total Recoverable Method 4181 (Spectrophotometric Infrared)
110795 1641 copy617 890 3883 TMA-WALTHAM copy007007
APPENDIX B
QUANTITY SURVEY DOCUMENTATION
TFMORAN INC Surveying - Engineering - Land Planning SoilsWetlands Mapping - Landscape Architecture
January 15 1996
Mr Jack Enos Vice President TFord Company Inc 118 Tenney Street Georgetown MA 01833
RE Survey Results - Salem Acres - SL4 Area Salem Massachusetts
Dear Jack
This letter amends the letter of December 13 1995 per our review last week
TFMoran Inc performed topographic surveys at the Salem Acres site on April 21 1994 for GEI Consultants prior to removal of material and for TFord Company on October 18 1995 after the removal of material The survey data from the original survey in 1994 was adjusted thirty feet higher to correct for a datum difference from current site datum This was due to the original reporting of the Site Benchmark (TP34) elevation as 11464 rather than 14464 which is the correct elevation
Once both topographic surfaces were on the site datum the raw cut volume was obtained by Eaglepoint (Volumes Module) Software utilizing the prismoidal method comparing the two surfaces For reference please see the attached topographic plan which superimposes the October 15 1995 contours (dark lines) over the April 21 1994 contours The volume is based on the intersection of the two surfaces Also it was noted that stock piles of material did exist on site which were not surveyed at the time
The final raw cut volume arrived at by the above methods is 12749 Cubic Yards
In November and December of 1995 the site was resurveyed to locate the area of exposed ledge at the site The results of this survey are shown on the attached topographic worksheet dated November 3 1995 and last revised January 15 1996 The results of the survey indicate the total site area to be 50860 sq ft or 117 acres The total area of exposed ledge surveyed is 19990 sq ft or 46 acres If you have any questions regarding the above call me directly Thank you
Sincerely
John W Myhaver Jr ^_ Field Operations Manager
Enclosure ItorLltr
Route 101 Bedford NH 03110 Phone (603) 472-4488 FAX (603) 472-9747
APPENDIX C
HEALTH AND SAFETY PHASE-OUT REPORT
HEALTH AND SAFETY PHASE-OUT REPORT SALEM ACRES SL-4 AREA
Introduction
During remediation work on SL-4 Health and Safety Monitoring was performed Cashins amp Associates Inc of Reading MA performed the following work as a subcontractor to TFCI
1) Preparation of a site-specific Health and Safety Plan (dated September 1 1995)
2) Provide a Field TechnicianIndustrial Hygienist to serve as Site Safety and Health Officer (SSHO) and to conduct air and noise monitoring
3) Provide a Certified Industrial Hygienist to review Health and Safety and to conduct site specific training (record of training included at end of Appendix C)
4) Collect 8-hour air samples for worker exposure and ambient air at the Barcelona Avenue gate Arrange for analysis of the samples and report results
5) Prepare daily and weekly Health and Safety reports
6) Prepare a Health and Safety Phase-Out Report
In general the following health and safety practices were followed
1) All workers wore hard hats safety glasses work boots gloves and hearing protection as minimum level PPE
2) When working in the exclusion zone workers wore in addition to above tyvek rubber overboots and rubber coated gloves When dust was a potential concern an industrial grade dustmist mask was also worn This level of PPE was considered Level D modified
3) Workers leaving the exclusion zone removed PPE (tyveks gloves boots and masks) in the support zone and either disposed of the items or decontaminated them
4) Workers andor visitors without 40-hour OSHA training were not permitted to enter the exclusion zone
Attached is a report prepared by Cashins amp Associates along with weekly Health and Safety Summary Reports prepared by the Field Hygienist In summary the air monitoring results indicate no levels exceeding the applicable exposure guidelines except one instance
During excavation of contaminated overburden in the northwest comer of the site an area of VOC contaminated soil was encountered Total VOCs levels measured using a PID exceeded the action level established in the Health and Safety Plan The SSHO advised TFCI to upgrade to Level C PPE in order to backfill the excavation in this area TFCI equipment operator upgraded and backfilled the area The SSHO in consultation with the Cashins CIH advised TFCI to avoid work in this area until the contaminants were characterized GEI sampled the material for waste characterization analysis and provided the results to TFCI Based on the results an action level was established by the CIH for the specific contaminants found Further PID measurements indicated levels below the new action level and work was resumed
The noise monitoring indicated that the noise level at the Barcelona Avenue gate was not exceeded Only one instance of excess noise level in the work zone was recorded (10 db(a) above the ambient noise level or 85 db(a)) Workers wore hearing protection in this instance
mdash 07171996 1601 6179444032 CASHIMS S ASSOCIATES PAGE 02
CASHINS amp Associates Inc
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July 17 1996
Mr Jack Enos T Ford Company Inc USTenney Street Georgetown MA 01833
Dear Jack
The Site Safety and Health Officer (SSHO) from Cashing amp Associates Inc performed daily inspections of the SL-4 area Salem Acres Superfund Site between 9595 and 12195 in accordance with the Health amp Safety Plan (HSP) for the site Daily inspection logs were submitted every day No accidentsincidents were reported during the work period
In accordance with the Health amp Safety Plan the SSHO performed daily air and noise monitoring at the site during Ac project Samples were collected for metals (lead beryllium chromium arsenic) and Polynuclear Aromatic Hydrocarbons (PAHs) at the site perimeter and for workers exposure determination Coal Tar Pitch Volatiles (a benzene soluble extractables) were also used to determine the workers exposure to PAH compounds Coal Tar Pitch Volatiles (CTPV) were analyzed using OSHA 58 Method If CTPV levels oq personal samples exceed the site criteria of 02 ragm3 the sample was submitted for PAHs analysis All air samples on the site perimeter were analyzed for PAH compounds
Site monitoring air sample collection and results report were done under the supervision of a Certified Industrial Hygienist
Full shift personal worker exposure samples were collected once a week Ambient air samples were collected at the Barcelona Avenue gate about 20 feet to the west of the site gate to determine if site contaminants were migrating off site The ambient air samples were also collected once a week during the project except on rainy days and days without work with contaminated soil
All air samples were analyzed by the American Industrial Hygiene Association accredited ESA Laboratories Inc using the following methods PAHs - NIOSH 5515 Lead - NIOSH 7082 Beryllium - NIOSH 7102 Chromium - NIOSH 7024 Arsenic - NIOSH 7900 Coal Tar Pitch Volatiles - OSHA 58 All methods used are accepted by the industrial hygiene community for 8-hour exposure assessment EPA methods are usually used for ambient air measurements
CRErORTTFOmiOO
80 Mam Street bull Reading MA 01867 bull Phone- 61 7-944-4060 bull Fax 61 7-944-4082
07171996 1601 6179444032 CASHIMS amp ASSOCIATES PAGE 03
The results of air samples for metals and PAHs are presented in Table No 1
All concentrations of metals and PAHs at the site perimeter (Barcelona Avenue) and active work zones were below the OSHA Permissible Exposure Limits (PEL) and the American Conference of Governmental Industrial Hygicnists Threshold Limit Value (ACGIH TLV) Two personal samples collected on October 19 and October 23rd showed Coal Tar Pitch Volatiles (CTPV) results above OSHA PEL and AIHA TLV limits Both samples were resubmittcd to the lab for further analysis to determine if PAH compounds are present because the CTPV results were above site criteria
The results of the PAH concentrations for the personal sample on Mark Goodwin on October 19 1995 during excavation and washing trucks and for the personal sample on Ron Maker on October 23 1995 during excavating and cleaning rocks by compressed air were below OSHA PEL and ACGIH TLV limits
The SSHO performed noise monitoring according to the HSP at the exclusion zone and at the Barcelona Avenue site perimeter fence A Dupont sound level meter was used for noise monitoring The noise level in the exclusion zone during all operations except one did not exceed the on site criteria of 85 dB(a) During a short time when the air compressor had been used to clean rocks the sound level in the exclusion zone next to the air compressor did exceed 85 dB(a) Ear protection devices were worn by the workers during that operation At no time did the noise level at the Barcelona Avenue site perimeter exceed 10 dB(a) above the ambient noise level or 85 dB(a)
The SSHO performed total dust monitoring on a daily basis during the project at the site perimeter downwind of work location and at the site gate using a Miniram real time dust meter The summary of dust monitoring is presented in Table No 2 Total dust concentrations on site and off site did not exceed site criteria of 1 mgm3 and the action level of 05 nigny1
The summary of air monitoring for Volatile Organic Compounds (VOC) is presented in Table No 3 VOC concentrations in the working area did not exceed the on site criteria of 5 ppm in a breathing zone VOC concentrations on the site perimeter did not exceed real time off site criteria of 2 ppm
Five detail reports with results of air sampling were submitted during the project period
Sincerely Cashins amp Associates Inc
Evelina Vaughan Industrial Hygieflfst
CASHINS amp ASSOCIATES Inc
80 Mam Street bull Reading MA 01867 bull Phone61 7-944-4060 bull Fax 617-944-4082
07171996 1601 6179444082 CASHINS S ASSOCIATES PAGE 04
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W3SXLY HBALTH amp SAFETY PLAN COMPLIANCE SUMMARY R3PORT
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LOCATION gal era Acres Sx^perfund Site 8L-4 Area
DATES INCLUDED IN SUMMARY
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LOCATION Salen Acres Suoerfund Site SL-4 Area
DATES INCLUDED IN SUMMARY
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WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
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LOCATION Salem Acres Superfund Site SL-4 Area
DATES INCLUDED IN SUMMARY
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LOCATION Salem Acres Superfund Site SL-4 Area
DATES INCLUDED IN SUMMARY J_
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WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
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LOCATION Salem Acres Superfund Site SL-4 Area
DATES INCLUDED IN SUMMARY T
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WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
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SUMMARIZED BY FOR CASMINS amp ASSOCIATES INC
55 CAMBRIDGE STREET bull SUITE 201 bull 8URUNGTON MA 01803 bull TEL 617-273-9080 bull FAX 617-273-90W
07151996 18 fO 6179444082 CASHINS S ASSOCIATES PAGE 02
CASHINS amp Associates Inc
WBBKLY HEALTH amp SAFETY FLAK COMPLIANCE SUMMARY REPORT
CLIENT T Ford Compapv
LOCATION i Sal am Acrlaquolaquo Suparfund Sita SL-4 Area
DATES INCLUDED IN SUMMARY i bull pound7 mdash
A 0-3 - A)
SXWMARIZ2D BY FOR CASHINS amp ASSOCIATES INC (
55 CAMBRIDGE STREET SUITE 201 bull SURtlNCTON MA 01803 TEL 617-273-9080 bull FAX 61 7-273-9084
- barcode 14732
- barcodetext SEMS Doc ID 14732
![Page 9: SALEM ACRES SUPERFUND SITE SALEM, MA ...The truck loading pa d consisted of a crushed stone are sea t up along the east sid e o f SL-4 adjacent to the access road A. row of concrete](https://reader036.vdocuments.us/reader036/viewer/2022070114/60729b840fec4e6b4d136a16/html5/thumbnails/9.jpg)
contaminated overburden Several techniques andor methods were used to clean bedrock including
a) Manual broom and shovel work b) Compressor with air gun to loosen material from crevices with water
used for dust control c) A Vac-All truck using water andor compressed air to loosen
material d) A broom attached to the bucket of an excavator
The surface of exposed bedrock was generally quite irregular and required considerable effort to remove soil and fly ash from cracks and crevices In some areas the rock is highly weathered and can be removed In these areas a determination was made in conjunction with GEI as to when to stop removal of weathered bedrock
During placement of random fill and loam some areas of exposed bedrock became re-covered with these earth materials TFCI proposed to topsoil and seed on these areas rather than re-cleaning the bedrock GEI EPA and MEC accepted this proposal
3 SITE RESTORATION
31 Random Fill
Random fill for the site restoration was obtained from a borrow pit located on Munson Street in Peabody MA GEI conducted confirmatory sampling of the borrow source The results are contained in the Demonstration of Compliance Report A grain size analysis is provided in Figure 1 A total of 1176 cy of random fill was delivered to the site and spread over all exposed soil subgrade areas The thickness is 6 inches except along the west side of the site where it ranges up to 5 ft thick where contaminated soil and fly ash were encountered at a deeper level (See Sec 4)
The random fill was spread and compacted using a CAT D4H dozer
32 Loam and Seeding
In the Spring of 1996 after Winter shutdown TFCI placed and spread a 6-inch layer of loam The loam was obtained from a loam stockpile located at a new residential subdivision in Ayer MA called Bennetts Brook and furnished to the site by D amp H Loam Company A total of 695 cy of loam was delivered to the site GEI conducted confirmatory sampling of the loam source The results are contained in the Demonstration of Compliance Report A topsoil analysis report is provided as
Figure 2
The loam was spread using a CAT D4H dozer Areas of the slope where the grade was steeper than 4HIV were first hand-seeded and then covered with Erosion Control and Revegetation Mat (ECRM) The entire loamed area was then hydro-seeded on May 14 1996 The seed used is Massachusetts Highway Department Specification M6030 Slope and Shoulder Mix
33 FencingDemobilization
In order to remove fly ash andor contaminated overburden which extended onto DA-1 it was necessary to remove the fence along the south side of DA-1 After completion of remediation work the fence was replaced Because of the winter shutdown TFCI reinstalled the fence prior to site restoration work to secure the DAshy1 area
Following placement of the random fill TFCI demobilized for winter shutdown Due to an early snowfall it was impossible to loam and seed the site prior to winter shutdown TFCI demobilized equipment and support facilities December 8-13 1995
In the Spring of 1996 it was only necessary to mobilize a dozer and small excavator to place and spread loam
4 QUANTITY SURVEYS AND AS-BUILT PLANS
41 Fly Ash Quantity Survey
In order to calculate the insitu quantity of fly ash for payment TFCI engaged a subcontractor T F Moran for survey work and quantity estimates T F Moran performed an existing conditions topographic survey on April 21 1994 for design studies conducted by GEI Consultants Inc This survey was updated and verified on September 8 1995 by T F Moran for TFCI In addition a stockpile of fly ash removed from SL-5 was also surveyed on this date
T F Moran surveyed the bottom of fly ash on October 18 1995 The results of the fly ash quantity surveys are shown on Figure 3 The quantities of fly ash are as follows
SL-4 Fly Ash 12750 cy SL-5 Fly Ash (stockpiled on SL-4) 520 cv
13270 cy
In addition there was an estimated 1500 cy of fly ash not included in the TF
Moran surveys because the material was in or under active stockpiles at the time of the survey The quantity survey and method of calculation is described in a letter from T F Moran dated January 15 1996 and contained in Appendix B
42 Limits of Remediation
In order to document the limits of remediation T F Moran surveyed the site on November 1 and December 5 1995 Areas where contaminated overburden were removed were surveyed at these times including the limits of exposed bedrock The results of these surveys are shown on Figure 4 The limits of SL-4 site remediation are as follows
Total Site Area Remediated 50860 sf Exposed Ledge 19990 sf
Site Restoration Area 30870 sf
In addition Area 1 is approximately 5416 sf
Note that the total quantity of contaminated overburden and fly ashsoildebris mixture was 6056 tons compared to the estimated 4100 tons from the design studies The primary reasons for the increase include the following
Incorporation of Area 1 from SL-5 in the SL-4 site remediation work
The northern limit of excavation extended further into DA-1 than anticipated in the RA Work Plan
Excavating further west into WA-1 than anticipated in the RA Work Plan
VOC contaminated fly ash and soil in the northwest corner near DAshy1 at a considerable thicknessdepth
The limits of remediation survey are described in the T F Moran letter contained in Appendix B
43 Final As-Built
A final as-built survey was performed by T F Moran on May 21 1996 The results of the survey are shown on Figure 5
TABLE 1 SUMMARY OF ASH REMOVAL
SALEM ACRES SUPERFUND SITE SL-4 AREA
DATE NOMBEraquo0poundLOADS
0AILY TOTAL ifrotfS) i
SEPTS 1 1750
SEPT 1 1 8 13470
SEPT 12 10 21080
SEPT 13 20 45800
SEPT 14 23 50100
SEPT 15 20 43160
SEPT 18 23 46870
SEPT 19 24 54780
SEPT 20 26 52800
SEPT 21 25 47700
SEPT 22 25 46915
SEPT 25 26 51950
SEPT 26 29 56820
SEPT 27 30 55660
SEPT 28 30 58410
SEPT 29 26 53520
OCT2 26 54600
OCT3 26 57000
OCT4 19 41080
OCT5 22 49240
OCT6 26 61860
OCT 10 18 47180
OCT 11 12 33860
OCT 13 17 439 40
OCT 17 3 7600
OCT 19 3 7720
CtnVfOtATIVE TOTAL (TONS)
1750
15220
36300
82100
132200
175360
222230
277010
329810
3775 10
424425
476375
5331 95
5888 55
647265
700785
755385
812385
853465
902705
9645 65
1011745
1045605
1089545
1097145
1104865
TABLE 2 SUMMARY OF CONTAMINATED
OVERBURDEN REMOVAL SALEM ACRES SUPERFUND SITE SL-4 AREA
DATE
on 19 OCT 20
OCT 23
OCT 24
OCT 25
OCT 26
OCT 27
OCT 31
NOV 1
NOV2
NOV 6
NOV 8
NOV 9
NOV 21
NOV 28
DEC 7
NUMBER OF LOADS
14
14
14
13
14
16
18
18
12
4
4
8
8
8
9
2
DAILY TOTAL (TONS)
46121
41649
49314
448 59
46225
48054
62358
56186
491 56
14209
14025
29010
27604
35513
33447
7885
CUMULATIVE TOTAL (TONS)
46121
87770
137084
181943
228168
276222
338580
394766
443922
458131
472156
501166
528770
564283
597730
6056 1 5
- -
--
Oct 17 1995 823PM P02 From LTTS OF Mfl INC PHONE No 617 438 S21S
GRftIN SIZE DISTRIBUTION TEST REPORT C c c e
100 i i ^ i i 7 ^ d bdquo bdquo j laquo ii i A j
bdquo9 bdquo
a 2 - a i
t sh
90 X
N^
B0 raquo m lts
-bull
70 Sk
gtia
Npound G0 shyu
550 gt
UJ bullshy
1u S pound 40 0 ^
30 bull i 20
10
0 2Q 0 1SG 100 10 01 aai 00UL
CRflIM CISC - mm
Test X +3 bull4 GRAVEL bull SflMD bull SILT bull DRY uses LL PI
t 16 00 2Z 3 521 256 SC-SM
SIEVE PERCENT FINCR STEVE PERCENT FINCR Uact on Incrwi nuwtoer ilz ilzi bull flUNSON ST PEABODC
bull bull a 96 3 4 777
15 95 10 714 1 92 e 20 607 Descr pt ion
075 90 40 505 bullSILTY CLAYEY GflNO 0 375 34 50 44 4
100 343
3X1 GRAIN SIZE 200 257
8804D60
gtDia Remarks
xC COEFh 1C1CNT5 UTS OF MASSACHUSETTS INC bull
SS1T to 1 u
Pro jlt-r t No UTS OF naSSACHLKKI lgt IMC Project) CftLCM flCHSCC
5 Richardson Lane
GtoneHam Mft 03 IBB Date 101195 Gamn 1 c- No 44fi1A
Figure 1
From UTS OF Mfl INC PHONE No 517 438 6216 Oct 17 1995 824PM F03
SOT ANALYSIS REPORT FOR NEW LAWN 101195
SOIL AND PLANT TISSUE TESTING LABWEST EXPERIMENT STATIONUNIVERSITY OF MASBACIIUfiFTTr AMHERST MA 01003
LAB NUMBER 3951010-107 BAG NUMBER 23467
DATE BFNT f
SOIL FROM COUNTY SOIL WEIGHT 537 g5cn CROP TURFORASS
UTS OF MASS INC COMMENTS ORGANIC MATTER 6 RICHARDSON LANE STONEHAM MA 02180
SAMPLE ID 4461B
LIMESTONE AND FERTILIZER RECOMMCNDATIONS FOR NEW LAWN CONSTRUCTION
No limestone ia required If peat mooc or similar material ia to be incorporated) see enclosed fact sheet
Fertilizer (per 10OO sq ft) 2 1ba N 2 Ibo P2O5 and O 1 bs KZO
Many fertilizer sources and rates may combine to provide acceptable turfgraes establ iahmont either from seed or aod One or two options baaed on this soil teat follow
Incorporate EITHER a 17-23-6 starter fert111zar at 10 lbs1000 sq ft OR a 30-3-3 lawn fertilizer at 7 1b81000 aq ft plus a 0-45-0 (triple superphosphate) fertilizer at 4 lbs1000 aq ft Hnto the top 3 to 4 inches of soil Retest Bull ona year after turf establishment
PLEASE read the enclosed fact sheets for niora specific Information on fertilization and liming procadurea
SOIL pH 71 NITROGEN NO3-N = Oa ppm NH4-N = 5 ppm BUFFER pH 74 ORGANIC MATTER 72 X (Desirable range 4-10X)
NUTRIENT_LEVELS_PPM_| Low Medium High Very High Phosphorus (P) 8 |XXXXXXXXXXXXX Potaaaium (K) 292 [XXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXX Calcium (Ca) 237S XXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXX Magnesium (Mg) 237 JXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXX
CATION EXCII CAP PERCENT BASE SATURATION MICRONUTRIENT LEVELS 130 Meq100g K= 52 Mg=134 Ca=816 ALL NORMAL
CXTRACTABLE ALUMINUM 41 ppm (Soil ranglaquo 10-250 ppm)
The lead level in thio soil 1s low
COMPUTER PROGRAM5-RECOMMENDATIONRbYOtHIOFPtANT~ampSOILSCI UMASS-AMHERST
Figure 2
TARGET SHEET
THE MATERIAL DESCRIBED BELOW WAS NOT SCANNED BECAUSE
(X) OVERSIZED
() NON-PAPER MEDIA
() OTHER
DESCRIPTION DOC 14732 DRAFT FINAL REMEDIAL CONSTRUCTION REPORT FIGURE 3 TOPOGRAPHIC PLAN SL-4 AREA BOTTOM OF FLY ASH SALEM ACRES SHEET 1 OF 1
THE OMITTED MATERIAL IS AVAILABLE FOR REVIEW BY APPOINTMENT
AT THE EPA NEW ENGLAND SUPERFUND RECORDS CENTER BOSTON MA
TARGET SHEET
THE MATERIAL DESCRIBED BELOW WAS NOT SCANNED BECAUSE
(X) OVERSIZED
() NON-PAPER MEDIA
() OTHER
DESCRIPTION DOC 14732 DRAFT FINAL REMEDIAL CONSTRUCTION REPORT FIGURE 4 TOPOGRAPHIC PLAN SL-4 AREA LIMIT OF REMEDIATION SALEM ACRES SHEET 1OF1
THE OMITTED MATERIAL IS AVAILABLE FOR REVIEW BY APPOINTMENT
AT THE EPA NEW ENGLAND SUPERFUND RECORDS CENTER BOSTON MA
TARGET SHEET
THE MATERIAL DESCRIBED BELOW WAS NOT SCANNED BECAUSE
(X) OVERSIZED
() NON-PAPER MEDIA
() OTHER
DESCRIPTION DOC 14732 DRAFT FINAL REMEDIAL CONSTRUCTION REPORT FIGURE 5 TOPOGRAPHIC PLAN SL-4 AREA AS-BUILT PLAN SALEM ACRES SHEET 1 OF 1
THE OMITTED MATERIAL IS AVAILABLE FOR REVIEW BY APPOINTMENT
AT THE EPA NEW ENGLAND SUPERFUND RECORDS CENTER BOSTON MA
(i)
^mft^m
VIEW OF BARCELONA AVENUE THROUGH ENTRANCE GATE PRECONT RUCTION
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(2)
VIEW OF ACCESS ROAD LOOKING NORTH SL-4 ON LEFT PRECONSTRUCTION
VIEW OF ACCESS ROAD LOOKING NORTH SL-4 ON LEFT DA-1 TO LEFT OF PICKUP TRUCK
PRECONSTRUCTION
(3)
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
O ID a CO z O OHI
CO UJ
OO_l
t CO ii-O
(5)
VIEW OF BOUNDARY BETWEEN SL-4 AND DA-1 LOOKING WEST PRECONSTRUCTION
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(6)
EROSION CONTROLS LOOKING NORTH FROM CORNER OF SL-4SL-5 ADJACENT TO WA-1 PRECONSTRUCTION
(7)
TRUCK LOADING PAD LOOKING NORTHWEST FROM SUPPORT ZONE
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(8)
DECONTAMINATION PAD LOOKING NORTHWEST FROM SUPPORT ZONE
(9)
EXCAVATION OF FLY ASH LOOKING NORTHWEST FROM CRZ NOTE WATER FOR DUST CONTROL
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(10)
VIEW LOOKING WEST AFTER REMOVAL OF FLY ASH NOTE WA-1 BEYOND EROSION CONTROLS
(11)
EXCAVATION OF CONTAMINATED OVERBURDEN LOOKING SOUTH FROM DA-1 BOUNDARY
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(12)
VIEW OF RESTORED SITE LOOKING WEST TOWARD WA-1
0
ltu
wsectbull
D Q
O
O z ^ O O_J LJJ
Q LJJ a o te LJJ
eg 3
(14)
VIEW OF RESTORED SITE LOOKING NORTH TOWARD DA-1 ALONG ACCESS ROAD
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(15)
gtbull bdquobdquo -
VIEW OF RESTORED SITE LOOKING SOUTH TOWARD SL-5
iu O
of bullo
01 u I ltO
w
o B ltabulls to 10
3
I Q Z
O m ^mdash
i sect^^ nu0 (- co^gtW IO - z zilaquo O O 5gl
oLU uj
V) LUo a o LU
(17)
VIEW OF RESTORED SITE ON DA-1 SJDE OF FENCE - LOOKING ST
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(18)
VIEW OF RESTORED SITE ON DA-1 SIDE OF FENCE - LOOKING WEST SL-4 ON RIGHT
APPENDIX A
ANALYTICAL RESULTS FOR
PONDED WATER
110795 1638 copy617 890 3883 TMA-WALTHAM ] 002007
PRELIMINARY REPORT UNAUDITED RESULTS
Thenno Analytical 300 Second Avenue PO Box 521 Waltham HA 02254
Attn Client Services Phone (617) 890-7200
Cashins amp Associates Order S5-11-034 55 Cambridge Street Date 110795 1522 Burlington HA 01803 Work ID Salem Acres Water
Date Received 110295 Attn Bob Cashins Date Completed
Purchase Order NA Invoice Number Client Code CASHINS
SAMPLE IDENTIFICATION
Sample Sample Number Description 01 11019S-924-01A
Sample Number 04
Sample Description
110195-9Z4-01D 02 110195-924-01B 05 110195-924-01E 03 110195-924-01C
Certified By
110795 1638 copy617 890 3883 TMA-WALTHAM 003007
PRELIMINARY REPORT UNAUDITED RESULTS
Order f S5-11-034 Thermo Analytical Page 2 110795 1522 TEST RESULTS BY SAHPLE
Test Description Volatile Organics- Aqueous Method EPA_8240 Test Code Collected 110195 02-00 Category WATER
DATE INJECTED 110695 DILUTION FACTOR 100 All results reported 1n ugL
COMPOUND RESULT DET LIMIT COMPOUND RESULT
Chloromethane U 10 Broroodi chl oromethane U Vinyl Chloride U 10 2-Chloroethyl Vinyl Ether U
Bromxnethane U 10 4-dethyl -2-pentanone U Chloroethane U 10 c1 3-1 3-Di chl oropropene U
Trichlorofluoronwthane U 50 Tol uene U Acetone 17 10 trans-1 3-Di chl oropropene LI
11-Oichloroethene U 50 11 2-Tri chl oroethane J Carbon Dlsulfide U 50 2-Hexanone U
Methyl ene Chloride U 50 Tetrachl oroethene U 12-Oichloroethene (total) U 50 D1 bromochl oromethane U
11-01 Chloroethane U 50 Chlorobenzene U Vinyl Acetate U 10 Ethyl benzene U
2-Butanone U 10 in and p-Xylene U Chloroform U 50 o-Xylene U
111-Tri Chloroethane U 50 Styrene U Carbon Tetrachlortde U 50 Broraoform U
Benzene U 50 112 2-Tat rachl oroethane U 12-01 Chloroethane U 50 1 3-01 chl orobenzene U
Trichloroethene U 50 I 4-Di chl orobenzene U 12-Dichloropropane U 50 12-01 chl orobenzene U
SURROGATE STANDARDS RESULT LEVEL X RECOVERY
12-Dichloroethane-D4 52 50 104 Toluene-08 47 50 94
l-Bromo-4-fluorobenzene 56 50 112
NOTES AND DEFINITIONS FOR THIS REPORT U =bull Undetected at stated detection limit
VOAJI
OET LIMIT
50 50
10 50 50 50 50 10
5 0 50 5 0 5 0 50 50 50 50 50 50 50 50
110795 1639 copy617 890 3883 TMA-WALTHAM copy004007
PRELIMINARY REPORT UNAUDITED RESULTS
Order t S5-11-034 Thermo Analytical Page 4 110795 1522 TEST RESULTS BY SAMPLE
ianple Description 110195-924-010 Lab No 04A Test Description RCRA Metals 1n Water Method SW846 Test Code
Collected 110195 0200 Category WATER
METAL RESULT DETECTION LIMIT METAL RESULT DETECTION LIMIT
Ag Silver U 10 As Arsenic 870 50
Ba Bar inn B69 10 Pb Lead U 50
Cd Cadmium U 50 Se Sel en1 um Z15 50
Cr Chromi um U 20 Hg Mercury U 020
NOTES AND DEFINITIONS FOR THIS REPORT All results reported in ugL U gt Undetected at stated detection limit
110795 1640 Q617 890 3883 TMA-WALTHAM 0005007
PRELIMINARY REPORT UNAUDITED RESULTS
Order S5-11-034 Thermo Analytical Page 5 110795 1522 REGULAR TEST RESULTS BY TEST
Chemical Oxygen Demand Mlnimun Maximum Method EPA600 4101
Sap Sample Description Result Units Limit Prepared Analyzed By 05A 110195-924-01E 64 bullgL 50 110395 110395 JD
Petroleum Hydrocarbons-H20 Minimum Maximum Method EPA600 4181
Samp Sample Description Result Units Limit Prepared Analyzed By 01A 110195-924-01A 108 mgL 050 110395 110395 JO
110795 1640 reg617 890 3883 TMA-WALTHAM copy006007
PRELIMINARY REPORT UNAUDITED RESULTS
Order I S5-11-034 Therm Analytical Page 6 110795 1522 TEST METHODOLOGIES
USEPA Test Methods for Evaluating Solid Wastes (SUS46 Third Edition) Method 7470 - Preparation of water for Mercury analysis
USEPA Test Methods for Evaluating Solid Vastes (SW846 Third Edition) Method 3010 - Add digestion of aqueous samples and extracts for total metals for analysis by Flame Atomic Absorption Spectroscopy or Inductively Coupled Plasma Spectroscopy
USEPA Test Methods for Evaluating Solid Vastes (SWB46 Third Edition Method 8270 mdash Gas ChroroatographyMass Spectrometry for PAHs
Volatile Organics in Water - Hazardous Substance List
SV846 Method 8240 - Modified
Test Methods for Evaluating Solid Waste SU-846 US EPA Office of Solid Waste and Emergency Response Washington 3rd Edition
Aqueous sanples are analyzed in accordance with Method 8240 using a purge and trap technique followed by 64s ChromatographyMass Spectroscopy
Quality assurance procedures for GCMS Include daily tuning and calibration of the mass spectrometer and the use of surrogate standards in each sample to monitor method performance Quantitatton is performed by the Internal standard method Analysis of blanks duplicate samples and standards are run frequently as further quality assurance procedures
USEPA Test Methods for Evaluating Solid Wastes (SW846 Third Edition) Method 3S10 mdash Separatory Funnel Liquid-Liquid Extraction
EPA-6004-79-020 - Chemical Oxygen Demand - Titrimetric Mid-Level Method 4101
EPA6004-79-020 - Petroleum Hydrocarbons 1n Water Total Recoverable Method 4181 (Spectrophotometric Infrared)
110795 1641 copy617 890 3883 TMA-WALTHAM copy007007
APPENDIX B
QUANTITY SURVEY DOCUMENTATION
TFMORAN INC Surveying - Engineering - Land Planning SoilsWetlands Mapping - Landscape Architecture
January 15 1996
Mr Jack Enos Vice President TFord Company Inc 118 Tenney Street Georgetown MA 01833
RE Survey Results - Salem Acres - SL4 Area Salem Massachusetts
Dear Jack
This letter amends the letter of December 13 1995 per our review last week
TFMoran Inc performed topographic surveys at the Salem Acres site on April 21 1994 for GEI Consultants prior to removal of material and for TFord Company on October 18 1995 after the removal of material The survey data from the original survey in 1994 was adjusted thirty feet higher to correct for a datum difference from current site datum This was due to the original reporting of the Site Benchmark (TP34) elevation as 11464 rather than 14464 which is the correct elevation
Once both topographic surfaces were on the site datum the raw cut volume was obtained by Eaglepoint (Volumes Module) Software utilizing the prismoidal method comparing the two surfaces For reference please see the attached topographic plan which superimposes the October 15 1995 contours (dark lines) over the April 21 1994 contours The volume is based on the intersection of the two surfaces Also it was noted that stock piles of material did exist on site which were not surveyed at the time
The final raw cut volume arrived at by the above methods is 12749 Cubic Yards
In November and December of 1995 the site was resurveyed to locate the area of exposed ledge at the site The results of this survey are shown on the attached topographic worksheet dated November 3 1995 and last revised January 15 1996 The results of the survey indicate the total site area to be 50860 sq ft or 117 acres The total area of exposed ledge surveyed is 19990 sq ft or 46 acres If you have any questions regarding the above call me directly Thank you
Sincerely
John W Myhaver Jr ^_ Field Operations Manager
Enclosure ItorLltr
Route 101 Bedford NH 03110 Phone (603) 472-4488 FAX (603) 472-9747
APPENDIX C
HEALTH AND SAFETY PHASE-OUT REPORT
HEALTH AND SAFETY PHASE-OUT REPORT SALEM ACRES SL-4 AREA
Introduction
During remediation work on SL-4 Health and Safety Monitoring was performed Cashins amp Associates Inc of Reading MA performed the following work as a subcontractor to TFCI
1) Preparation of a site-specific Health and Safety Plan (dated September 1 1995)
2) Provide a Field TechnicianIndustrial Hygienist to serve as Site Safety and Health Officer (SSHO) and to conduct air and noise monitoring
3) Provide a Certified Industrial Hygienist to review Health and Safety and to conduct site specific training (record of training included at end of Appendix C)
4) Collect 8-hour air samples for worker exposure and ambient air at the Barcelona Avenue gate Arrange for analysis of the samples and report results
5) Prepare daily and weekly Health and Safety reports
6) Prepare a Health and Safety Phase-Out Report
In general the following health and safety practices were followed
1) All workers wore hard hats safety glasses work boots gloves and hearing protection as minimum level PPE
2) When working in the exclusion zone workers wore in addition to above tyvek rubber overboots and rubber coated gloves When dust was a potential concern an industrial grade dustmist mask was also worn This level of PPE was considered Level D modified
3) Workers leaving the exclusion zone removed PPE (tyveks gloves boots and masks) in the support zone and either disposed of the items or decontaminated them
4) Workers andor visitors without 40-hour OSHA training were not permitted to enter the exclusion zone
Attached is a report prepared by Cashins amp Associates along with weekly Health and Safety Summary Reports prepared by the Field Hygienist In summary the air monitoring results indicate no levels exceeding the applicable exposure guidelines except one instance
During excavation of contaminated overburden in the northwest comer of the site an area of VOC contaminated soil was encountered Total VOCs levels measured using a PID exceeded the action level established in the Health and Safety Plan The SSHO advised TFCI to upgrade to Level C PPE in order to backfill the excavation in this area TFCI equipment operator upgraded and backfilled the area The SSHO in consultation with the Cashins CIH advised TFCI to avoid work in this area until the contaminants were characterized GEI sampled the material for waste characterization analysis and provided the results to TFCI Based on the results an action level was established by the CIH for the specific contaminants found Further PID measurements indicated levels below the new action level and work was resumed
The noise monitoring indicated that the noise level at the Barcelona Avenue gate was not exceeded Only one instance of excess noise level in the work zone was recorded (10 db(a) above the ambient noise level or 85 db(a)) Workers wore hearing protection in this instance
mdash 07171996 1601 6179444032 CASHIMS S ASSOCIATES PAGE 02
CASHINS amp Associates Inc
ItxhalrM Hy-gifnr A Invtronmtnltl Tttling
July 17 1996
Mr Jack Enos T Ford Company Inc USTenney Street Georgetown MA 01833
Dear Jack
The Site Safety and Health Officer (SSHO) from Cashing amp Associates Inc performed daily inspections of the SL-4 area Salem Acres Superfund Site between 9595 and 12195 in accordance with the Health amp Safety Plan (HSP) for the site Daily inspection logs were submitted every day No accidentsincidents were reported during the work period
In accordance with the Health amp Safety Plan the SSHO performed daily air and noise monitoring at the site during Ac project Samples were collected for metals (lead beryllium chromium arsenic) and Polynuclear Aromatic Hydrocarbons (PAHs) at the site perimeter and for workers exposure determination Coal Tar Pitch Volatiles (a benzene soluble extractables) were also used to determine the workers exposure to PAH compounds Coal Tar Pitch Volatiles (CTPV) were analyzed using OSHA 58 Method If CTPV levels oq personal samples exceed the site criteria of 02 ragm3 the sample was submitted for PAHs analysis All air samples on the site perimeter were analyzed for PAH compounds
Site monitoring air sample collection and results report were done under the supervision of a Certified Industrial Hygienist
Full shift personal worker exposure samples were collected once a week Ambient air samples were collected at the Barcelona Avenue gate about 20 feet to the west of the site gate to determine if site contaminants were migrating off site The ambient air samples were also collected once a week during the project except on rainy days and days without work with contaminated soil
All air samples were analyzed by the American Industrial Hygiene Association accredited ESA Laboratories Inc using the following methods PAHs - NIOSH 5515 Lead - NIOSH 7082 Beryllium - NIOSH 7102 Chromium - NIOSH 7024 Arsenic - NIOSH 7900 Coal Tar Pitch Volatiles - OSHA 58 All methods used are accepted by the industrial hygiene community for 8-hour exposure assessment EPA methods are usually used for ambient air measurements
CRErORTTFOmiOO
80 Mam Street bull Reading MA 01867 bull Phone- 61 7-944-4060 bull Fax 61 7-944-4082
07171996 1601 6179444032 CASHIMS amp ASSOCIATES PAGE 03
The results of air samples for metals and PAHs are presented in Table No 1
All concentrations of metals and PAHs at the site perimeter (Barcelona Avenue) and active work zones were below the OSHA Permissible Exposure Limits (PEL) and the American Conference of Governmental Industrial Hygicnists Threshold Limit Value (ACGIH TLV) Two personal samples collected on October 19 and October 23rd showed Coal Tar Pitch Volatiles (CTPV) results above OSHA PEL and AIHA TLV limits Both samples were resubmittcd to the lab for further analysis to determine if PAH compounds are present because the CTPV results were above site criteria
The results of the PAH concentrations for the personal sample on Mark Goodwin on October 19 1995 during excavation and washing trucks and for the personal sample on Ron Maker on October 23 1995 during excavating and cleaning rocks by compressed air were below OSHA PEL and ACGIH TLV limits
The SSHO performed noise monitoring according to the HSP at the exclusion zone and at the Barcelona Avenue site perimeter fence A Dupont sound level meter was used for noise monitoring The noise level in the exclusion zone during all operations except one did not exceed the on site criteria of 85 dB(a) During a short time when the air compressor had been used to clean rocks the sound level in the exclusion zone next to the air compressor did exceed 85 dB(a) Ear protection devices were worn by the workers during that operation At no time did the noise level at the Barcelona Avenue site perimeter exceed 10 dB(a) above the ambient noise level or 85 dB(a)
The SSHO performed total dust monitoring on a daily basis during the project at the site perimeter downwind of work location and at the site gate using a Miniram real time dust meter The summary of dust monitoring is presented in Table No 2 Total dust concentrations on site and off site did not exceed site criteria of 1 mgm3 and the action level of 05 nigny1
The summary of air monitoring for Volatile Organic Compounds (VOC) is presented in Table No 3 VOC concentrations in the working area did not exceed the on site criteria of 5 ppm in a breathing zone VOC concentrations on the site perimeter did not exceed real time off site criteria of 2 ppm
Five detail reports with results of air sampling were submitted during the project period
Sincerely Cashins amp Associates Inc
Evelina Vaughan Industrial Hygieflfst
CASHINS amp ASSOCIATES Inc
80 Mam Street bull Reading MA 01867 bull Phone61 7-944-4060 bull Fax 617-944-4082
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CASHINS amp Associates inc
Ifxtuitral Hygltne A fnvironmtnltt Tuning
W3SXLY HBALTH amp SAFETY PLAN COMPLIANCE SUMMARY R3PORT
CLIENT T foyd C o m a n
LOCATION gal era Acres Sx^perfund Site 8L-4 Area
DATES INCLUDED IN SUMMARY
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55 CAMBRIDGE STREET bull SUITE 201 bull BURLINGTON MA 01803 laquo TEL 61 -273-9080 bull FAX 67-273-9C84
09111995 1023 6172739084 CASHINS ASSOCIATES PAGE 01
CASHINSamp Associates Inc
Induttrml Hygttnr t Emtroomtnttl Ttstinf
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Fprd Company
LOCATION Salen Acres Suoerfund Site SL-4 Area
DATES INCLUDED IN SUMMARY
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55 CAMBRIDGE STREET bull SUITE 201 bull BURLINGTON MA 01803 raquo- TEL 6J 7-273-9080 bull FAX 617-273-9084
CASHINS amp Associates Inc
Industrial Hygitnf amp CmimnmenUl Tinting
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Compan
LOCATION Salem Acres Superfund Site SL-4 Area
DATES INCLUDED IN SUMMARY
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DATES INCLUDED IN SUMMARY
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07161996 1650 6179444082 CASH INS amp ASSOCIATES PAGE 08
CASHINSamp Associates Inc
Intutttitl Myffcnt t InvtmnmmUt Itnl
WEEKLY HEALTH 6 SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Fortjl Cqjapany
LOCATION Salem Acrlaquoa Superfund Site 9L-4 Area
DATES INCLUDED IN SUMMARY
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55 CAMBRIDGE STREFT SUITE 201 bull BURUNCTON MA oisoa bull TEL 617-273-9030 bull FAX 6i 7-273-9084
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Industrial Hygiene amp Emironmvntal Testing
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Company
LOCATION Salem Acres Superfund Site SL-4 Area
DATES INCLUDED IN SUMMARY J_
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PROJECT NAME_ SITE LOCATION
THE PURPOSE OF THE FOLLOWING STATEMENT IS TO DOCUMENT THE EXISTENCE OF A CONDITION OR CONCERN WHICH CASHINS amp ASSOCIATES INC BELIEVES WARRANTS IMMEDIATE CORRECTIVE ACTION POSSIBLE SOLUTIONS AND OR CORRECTIVE ACTIONS WILL BE INCLUDED IN THIS NOTIFICATION WHEN POSSIBLE THIS NOTIFICATION IS LIMITED TO SITUATIONS THAT REPRESENT EITHER IMMEDIATE DANGER TO LIFE OR HEALTH CONDITIONS OR PREVIOUSLY IDENTIFIED CHRONIC PROBLEMS THAT UNDERMINE OUR ABILITY TO EFFECTIVELY INSURE COMPLIANCE WITH THE REQUIREMENTS OF THE HEALTH AND SAFETY PLAN
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CISHINS amp Associates Inc
Industrial Hygirne amp Cmimnmtntal Testing
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Company
LOCATION Salem Acres Superfund Site SL-4 Area
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07161996 1650 617944408 CASHING 3 ASSOCIATES PAGE 05
CASHINSamp Associates Inc
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CASHIMS amp ASSOCIATES PAGE 04 07161996 1658 6179444032
OVSHINSamp Associates Inc
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Company T
LOCATION Salem AcrM Suoerfund Stta 8L-4 Araa
DATES INCLUDED IN SUMMARY
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55 CAMBRIDGE STREET bull SUITE 201 bull BURUNGTON MA 01803 bull TEL 617-273-9080 bull FAX 617-273-9084
07161996 1658 6179444082 CASHIMS 3 ASSOCIATES PAGE 03
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55 CAMBRIDGE STREET bull SUITE 201 bull 8URUNGTON MA 01803 bull TEL 617-273-9080 bull FAX 617-273-90W
07151996 18 fO 6179444082 CASHINS S ASSOCIATES PAGE 02
CASHINS amp Associates Inc
WBBKLY HEALTH amp SAFETY FLAK COMPLIANCE SUMMARY REPORT
CLIENT T Ford Compapv
LOCATION i Sal am Acrlaquolaquo Suparfund Sita SL-4 Area
DATES INCLUDED IN SUMMARY i bull pound7 mdash
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- barcode 14732
- barcodetext SEMS Doc ID 14732
![Page 10: SALEM ACRES SUPERFUND SITE SALEM, MA ...The truck loading pa d consisted of a crushed stone are sea t up along the east sid e o f SL-4 adjacent to the access road A. row of concrete](https://reader036.vdocuments.us/reader036/viewer/2022070114/60729b840fec4e6b4d136a16/html5/thumbnails/10.jpg)
Figure 2
The loam was spread using a CAT D4H dozer Areas of the slope where the grade was steeper than 4HIV were first hand-seeded and then covered with Erosion Control and Revegetation Mat (ECRM) The entire loamed area was then hydro-seeded on May 14 1996 The seed used is Massachusetts Highway Department Specification M6030 Slope and Shoulder Mix
33 FencingDemobilization
In order to remove fly ash andor contaminated overburden which extended onto DA-1 it was necessary to remove the fence along the south side of DA-1 After completion of remediation work the fence was replaced Because of the winter shutdown TFCI reinstalled the fence prior to site restoration work to secure the DAshy1 area
Following placement of the random fill TFCI demobilized for winter shutdown Due to an early snowfall it was impossible to loam and seed the site prior to winter shutdown TFCI demobilized equipment and support facilities December 8-13 1995
In the Spring of 1996 it was only necessary to mobilize a dozer and small excavator to place and spread loam
4 QUANTITY SURVEYS AND AS-BUILT PLANS
41 Fly Ash Quantity Survey
In order to calculate the insitu quantity of fly ash for payment TFCI engaged a subcontractor T F Moran for survey work and quantity estimates T F Moran performed an existing conditions topographic survey on April 21 1994 for design studies conducted by GEI Consultants Inc This survey was updated and verified on September 8 1995 by T F Moran for TFCI In addition a stockpile of fly ash removed from SL-5 was also surveyed on this date
T F Moran surveyed the bottom of fly ash on October 18 1995 The results of the fly ash quantity surveys are shown on Figure 3 The quantities of fly ash are as follows
SL-4 Fly Ash 12750 cy SL-5 Fly Ash (stockpiled on SL-4) 520 cv
13270 cy
In addition there was an estimated 1500 cy of fly ash not included in the TF
Moran surveys because the material was in or under active stockpiles at the time of the survey The quantity survey and method of calculation is described in a letter from T F Moran dated January 15 1996 and contained in Appendix B
42 Limits of Remediation
In order to document the limits of remediation T F Moran surveyed the site on November 1 and December 5 1995 Areas where contaminated overburden were removed were surveyed at these times including the limits of exposed bedrock The results of these surveys are shown on Figure 4 The limits of SL-4 site remediation are as follows
Total Site Area Remediated 50860 sf Exposed Ledge 19990 sf
Site Restoration Area 30870 sf
In addition Area 1 is approximately 5416 sf
Note that the total quantity of contaminated overburden and fly ashsoildebris mixture was 6056 tons compared to the estimated 4100 tons from the design studies The primary reasons for the increase include the following
Incorporation of Area 1 from SL-5 in the SL-4 site remediation work
The northern limit of excavation extended further into DA-1 than anticipated in the RA Work Plan
Excavating further west into WA-1 than anticipated in the RA Work Plan
VOC contaminated fly ash and soil in the northwest corner near DAshy1 at a considerable thicknessdepth
The limits of remediation survey are described in the T F Moran letter contained in Appendix B
43 Final As-Built
A final as-built survey was performed by T F Moran on May 21 1996 The results of the survey are shown on Figure 5
TABLE 1 SUMMARY OF ASH REMOVAL
SALEM ACRES SUPERFUND SITE SL-4 AREA
DATE NOMBEraquo0poundLOADS
0AILY TOTAL ifrotfS) i
SEPTS 1 1750
SEPT 1 1 8 13470
SEPT 12 10 21080
SEPT 13 20 45800
SEPT 14 23 50100
SEPT 15 20 43160
SEPT 18 23 46870
SEPT 19 24 54780
SEPT 20 26 52800
SEPT 21 25 47700
SEPT 22 25 46915
SEPT 25 26 51950
SEPT 26 29 56820
SEPT 27 30 55660
SEPT 28 30 58410
SEPT 29 26 53520
OCT2 26 54600
OCT3 26 57000
OCT4 19 41080
OCT5 22 49240
OCT6 26 61860
OCT 10 18 47180
OCT 11 12 33860
OCT 13 17 439 40
OCT 17 3 7600
OCT 19 3 7720
CtnVfOtATIVE TOTAL (TONS)
1750
15220
36300
82100
132200
175360
222230
277010
329810
3775 10
424425
476375
5331 95
5888 55
647265
700785
755385
812385
853465
902705
9645 65
1011745
1045605
1089545
1097145
1104865
TABLE 2 SUMMARY OF CONTAMINATED
OVERBURDEN REMOVAL SALEM ACRES SUPERFUND SITE SL-4 AREA
DATE
on 19 OCT 20
OCT 23
OCT 24
OCT 25
OCT 26
OCT 27
OCT 31
NOV 1
NOV2
NOV 6
NOV 8
NOV 9
NOV 21
NOV 28
DEC 7
NUMBER OF LOADS
14
14
14
13
14
16
18
18
12
4
4
8
8
8
9
2
DAILY TOTAL (TONS)
46121
41649
49314
448 59
46225
48054
62358
56186
491 56
14209
14025
29010
27604
35513
33447
7885
CUMULATIVE TOTAL (TONS)
46121
87770
137084
181943
228168
276222
338580
394766
443922
458131
472156
501166
528770
564283
597730
6056 1 5
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GtoneHam Mft 03 IBB Date 101195 Gamn 1 c- No 44fi1A
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From UTS OF Mfl INC PHONE No 517 438 6216 Oct 17 1995 824PM F03
SOT ANALYSIS REPORT FOR NEW LAWN 101195
SOIL AND PLANT TISSUE TESTING LABWEST EXPERIMENT STATIONUNIVERSITY OF MASBACIIUfiFTTr AMHERST MA 01003
LAB NUMBER 3951010-107 BAG NUMBER 23467
DATE BFNT f
SOIL FROM COUNTY SOIL WEIGHT 537 g5cn CROP TURFORASS
UTS OF MASS INC COMMENTS ORGANIC MATTER 6 RICHARDSON LANE STONEHAM MA 02180
SAMPLE ID 4461B
LIMESTONE AND FERTILIZER RECOMMCNDATIONS FOR NEW LAWN CONSTRUCTION
No limestone ia required If peat mooc or similar material ia to be incorporated) see enclosed fact sheet
Fertilizer (per 10OO sq ft) 2 1ba N 2 Ibo P2O5 and O 1 bs KZO
Many fertilizer sources and rates may combine to provide acceptable turfgraes establ iahmont either from seed or aod One or two options baaed on this soil teat follow
Incorporate EITHER a 17-23-6 starter fert111zar at 10 lbs1000 sq ft OR a 30-3-3 lawn fertilizer at 7 1b81000 aq ft plus a 0-45-0 (triple superphosphate) fertilizer at 4 lbs1000 aq ft Hnto the top 3 to 4 inches of soil Retest Bull ona year after turf establishment
PLEASE read the enclosed fact sheets for niora specific Information on fertilization and liming procadurea
SOIL pH 71 NITROGEN NO3-N = Oa ppm NH4-N = 5 ppm BUFFER pH 74 ORGANIC MATTER 72 X (Desirable range 4-10X)
NUTRIENT_LEVELS_PPM_| Low Medium High Very High Phosphorus (P) 8 |XXXXXXXXXXXXX Potaaaium (K) 292 [XXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXX Calcium (Ca) 237S XXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXX Magnesium (Mg) 237 JXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXX
CATION EXCII CAP PERCENT BASE SATURATION MICRONUTRIENT LEVELS 130 Meq100g K= 52 Mg=134 Ca=816 ALL NORMAL
CXTRACTABLE ALUMINUM 41 ppm (Soil ranglaquo 10-250 ppm)
The lead level in thio soil 1s low
COMPUTER PROGRAM5-RECOMMENDATIONRbYOtHIOFPtANT~ampSOILSCI UMASS-AMHERST
Figure 2
TARGET SHEET
THE MATERIAL DESCRIBED BELOW WAS NOT SCANNED BECAUSE
(X) OVERSIZED
() NON-PAPER MEDIA
() OTHER
DESCRIPTION DOC 14732 DRAFT FINAL REMEDIAL CONSTRUCTION REPORT FIGURE 3 TOPOGRAPHIC PLAN SL-4 AREA BOTTOM OF FLY ASH SALEM ACRES SHEET 1 OF 1
THE OMITTED MATERIAL IS AVAILABLE FOR REVIEW BY APPOINTMENT
AT THE EPA NEW ENGLAND SUPERFUND RECORDS CENTER BOSTON MA
TARGET SHEET
THE MATERIAL DESCRIBED BELOW WAS NOT SCANNED BECAUSE
(X) OVERSIZED
() NON-PAPER MEDIA
() OTHER
DESCRIPTION DOC 14732 DRAFT FINAL REMEDIAL CONSTRUCTION REPORT FIGURE 4 TOPOGRAPHIC PLAN SL-4 AREA LIMIT OF REMEDIATION SALEM ACRES SHEET 1OF1
THE OMITTED MATERIAL IS AVAILABLE FOR REVIEW BY APPOINTMENT
AT THE EPA NEW ENGLAND SUPERFUND RECORDS CENTER BOSTON MA
TARGET SHEET
THE MATERIAL DESCRIBED BELOW WAS NOT SCANNED BECAUSE
(X) OVERSIZED
() NON-PAPER MEDIA
() OTHER
DESCRIPTION DOC 14732 DRAFT FINAL REMEDIAL CONSTRUCTION REPORT FIGURE 5 TOPOGRAPHIC PLAN SL-4 AREA AS-BUILT PLAN SALEM ACRES SHEET 1 OF 1
THE OMITTED MATERIAL IS AVAILABLE FOR REVIEW BY APPOINTMENT
AT THE EPA NEW ENGLAND SUPERFUND RECORDS CENTER BOSTON MA
(i)
^mft^m
VIEW OF BARCELONA AVENUE THROUGH ENTRANCE GATE PRECONT RUCTION
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(2)
VIEW OF ACCESS ROAD LOOKING NORTH SL-4 ON LEFT PRECONSTRUCTION
VIEW OF ACCESS ROAD LOOKING NORTH SL-4 ON LEFT DA-1 TO LEFT OF PICKUP TRUCK
PRECONSTRUCTION
(3)
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
O ID a CO z O OHI
CO UJ
OO_l
t CO ii-O
(5)
VIEW OF BOUNDARY BETWEEN SL-4 AND DA-1 LOOKING WEST PRECONSTRUCTION
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(6)
EROSION CONTROLS LOOKING NORTH FROM CORNER OF SL-4SL-5 ADJACENT TO WA-1 PRECONSTRUCTION
(7)
TRUCK LOADING PAD LOOKING NORTHWEST FROM SUPPORT ZONE
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(8)
DECONTAMINATION PAD LOOKING NORTHWEST FROM SUPPORT ZONE
(9)
EXCAVATION OF FLY ASH LOOKING NORTHWEST FROM CRZ NOTE WATER FOR DUST CONTROL
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(10)
VIEW LOOKING WEST AFTER REMOVAL OF FLY ASH NOTE WA-1 BEYOND EROSION CONTROLS
(11)
EXCAVATION OF CONTAMINATED OVERBURDEN LOOKING SOUTH FROM DA-1 BOUNDARY
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(12)
VIEW OF RESTORED SITE LOOKING WEST TOWARD WA-1
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VIEW OF RESTORED SITE LOOKING NORTH TOWARD DA-1 ALONG ACCESS ROAD
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(15)
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VIEW OF RESTORED SITE ON DA-1 SJDE OF FENCE - LOOKING ST
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(18)
VIEW OF RESTORED SITE ON DA-1 SIDE OF FENCE - LOOKING WEST SL-4 ON RIGHT
APPENDIX A
ANALYTICAL RESULTS FOR
PONDED WATER
110795 1638 copy617 890 3883 TMA-WALTHAM ] 002007
PRELIMINARY REPORT UNAUDITED RESULTS
Thenno Analytical 300 Second Avenue PO Box 521 Waltham HA 02254
Attn Client Services Phone (617) 890-7200
Cashins amp Associates Order S5-11-034 55 Cambridge Street Date 110795 1522 Burlington HA 01803 Work ID Salem Acres Water
Date Received 110295 Attn Bob Cashins Date Completed
Purchase Order NA Invoice Number Client Code CASHINS
SAMPLE IDENTIFICATION
Sample Sample Number Description 01 11019S-924-01A
Sample Number 04
Sample Description
110195-9Z4-01D 02 110195-924-01B 05 110195-924-01E 03 110195-924-01C
Certified By
110795 1638 copy617 890 3883 TMA-WALTHAM 003007
PRELIMINARY REPORT UNAUDITED RESULTS
Order f S5-11-034 Thermo Analytical Page 2 110795 1522 TEST RESULTS BY SAHPLE
Test Description Volatile Organics- Aqueous Method EPA_8240 Test Code Collected 110195 02-00 Category WATER
DATE INJECTED 110695 DILUTION FACTOR 100 All results reported 1n ugL
COMPOUND RESULT DET LIMIT COMPOUND RESULT
Chloromethane U 10 Broroodi chl oromethane U Vinyl Chloride U 10 2-Chloroethyl Vinyl Ether U
Bromxnethane U 10 4-dethyl -2-pentanone U Chloroethane U 10 c1 3-1 3-Di chl oropropene U
Trichlorofluoronwthane U 50 Tol uene U Acetone 17 10 trans-1 3-Di chl oropropene LI
11-Oichloroethene U 50 11 2-Tri chl oroethane J Carbon Dlsulfide U 50 2-Hexanone U
Methyl ene Chloride U 50 Tetrachl oroethene U 12-Oichloroethene (total) U 50 D1 bromochl oromethane U
11-01 Chloroethane U 50 Chlorobenzene U Vinyl Acetate U 10 Ethyl benzene U
2-Butanone U 10 in and p-Xylene U Chloroform U 50 o-Xylene U
111-Tri Chloroethane U 50 Styrene U Carbon Tetrachlortde U 50 Broraoform U
Benzene U 50 112 2-Tat rachl oroethane U 12-01 Chloroethane U 50 1 3-01 chl orobenzene U
Trichloroethene U 50 I 4-Di chl orobenzene U 12-Dichloropropane U 50 12-01 chl orobenzene U
SURROGATE STANDARDS RESULT LEVEL X RECOVERY
12-Dichloroethane-D4 52 50 104 Toluene-08 47 50 94
l-Bromo-4-fluorobenzene 56 50 112
NOTES AND DEFINITIONS FOR THIS REPORT U =bull Undetected at stated detection limit
VOAJI
OET LIMIT
50 50
10 50 50 50 50 10
5 0 50 5 0 5 0 50 50 50 50 50 50 50 50
110795 1639 copy617 890 3883 TMA-WALTHAM copy004007
PRELIMINARY REPORT UNAUDITED RESULTS
Order t S5-11-034 Thermo Analytical Page 4 110795 1522 TEST RESULTS BY SAMPLE
ianple Description 110195-924-010 Lab No 04A Test Description RCRA Metals 1n Water Method SW846 Test Code
Collected 110195 0200 Category WATER
METAL RESULT DETECTION LIMIT METAL RESULT DETECTION LIMIT
Ag Silver U 10 As Arsenic 870 50
Ba Bar inn B69 10 Pb Lead U 50
Cd Cadmium U 50 Se Sel en1 um Z15 50
Cr Chromi um U 20 Hg Mercury U 020
NOTES AND DEFINITIONS FOR THIS REPORT All results reported in ugL U gt Undetected at stated detection limit
110795 1640 Q617 890 3883 TMA-WALTHAM 0005007
PRELIMINARY REPORT UNAUDITED RESULTS
Order S5-11-034 Thermo Analytical Page 5 110795 1522 REGULAR TEST RESULTS BY TEST
Chemical Oxygen Demand Mlnimun Maximum Method EPA600 4101
Sap Sample Description Result Units Limit Prepared Analyzed By 05A 110195-924-01E 64 bullgL 50 110395 110395 JD
Petroleum Hydrocarbons-H20 Minimum Maximum Method EPA600 4181
Samp Sample Description Result Units Limit Prepared Analyzed By 01A 110195-924-01A 108 mgL 050 110395 110395 JO
110795 1640 reg617 890 3883 TMA-WALTHAM copy006007
PRELIMINARY REPORT UNAUDITED RESULTS
Order I S5-11-034 Therm Analytical Page 6 110795 1522 TEST METHODOLOGIES
USEPA Test Methods for Evaluating Solid Wastes (SUS46 Third Edition) Method 7470 - Preparation of water for Mercury analysis
USEPA Test Methods for Evaluating Solid Vastes (SW846 Third Edition) Method 3010 - Add digestion of aqueous samples and extracts for total metals for analysis by Flame Atomic Absorption Spectroscopy or Inductively Coupled Plasma Spectroscopy
USEPA Test Methods for Evaluating Solid Vastes (SWB46 Third Edition Method 8270 mdash Gas ChroroatographyMass Spectrometry for PAHs
Volatile Organics in Water - Hazardous Substance List
SV846 Method 8240 - Modified
Test Methods for Evaluating Solid Waste SU-846 US EPA Office of Solid Waste and Emergency Response Washington 3rd Edition
Aqueous sanples are analyzed in accordance with Method 8240 using a purge and trap technique followed by 64s ChromatographyMass Spectroscopy
Quality assurance procedures for GCMS Include daily tuning and calibration of the mass spectrometer and the use of surrogate standards in each sample to monitor method performance Quantitatton is performed by the Internal standard method Analysis of blanks duplicate samples and standards are run frequently as further quality assurance procedures
USEPA Test Methods for Evaluating Solid Wastes (SW846 Third Edition) Method 3S10 mdash Separatory Funnel Liquid-Liquid Extraction
EPA-6004-79-020 - Chemical Oxygen Demand - Titrimetric Mid-Level Method 4101
EPA6004-79-020 - Petroleum Hydrocarbons 1n Water Total Recoverable Method 4181 (Spectrophotometric Infrared)
110795 1641 copy617 890 3883 TMA-WALTHAM copy007007
APPENDIX B
QUANTITY SURVEY DOCUMENTATION
TFMORAN INC Surveying - Engineering - Land Planning SoilsWetlands Mapping - Landscape Architecture
January 15 1996
Mr Jack Enos Vice President TFord Company Inc 118 Tenney Street Georgetown MA 01833
RE Survey Results - Salem Acres - SL4 Area Salem Massachusetts
Dear Jack
This letter amends the letter of December 13 1995 per our review last week
TFMoran Inc performed topographic surveys at the Salem Acres site on April 21 1994 for GEI Consultants prior to removal of material and for TFord Company on October 18 1995 after the removal of material The survey data from the original survey in 1994 was adjusted thirty feet higher to correct for a datum difference from current site datum This was due to the original reporting of the Site Benchmark (TP34) elevation as 11464 rather than 14464 which is the correct elevation
Once both topographic surfaces were on the site datum the raw cut volume was obtained by Eaglepoint (Volumes Module) Software utilizing the prismoidal method comparing the two surfaces For reference please see the attached topographic plan which superimposes the October 15 1995 contours (dark lines) over the April 21 1994 contours The volume is based on the intersection of the two surfaces Also it was noted that stock piles of material did exist on site which were not surveyed at the time
The final raw cut volume arrived at by the above methods is 12749 Cubic Yards
In November and December of 1995 the site was resurveyed to locate the area of exposed ledge at the site The results of this survey are shown on the attached topographic worksheet dated November 3 1995 and last revised January 15 1996 The results of the survey indicate the total site area to be 50860 sq ft or 117 acres The total area of exposed ledge surveyed is 19990 sq ft or 46 acres If you have any questions regarding the above call me directly Thank you
Sincerely
John W Myhaver Jr ^_ Field Operations Manager
Enclosure ItorLltr
Route 101 Bedford NH 03110 Phone (603) 472-4488 FAX (603) 472-9747
APPENDIX C
HEALTH AND SAFETY PHASE-OUT REPORT
HEALTH AND SAFETY PHASE-OUT REPORT SALEM ACRES SL-4 AREA
Introduction
During remediation work on SL-4 Health and Safety Monitoring was performed Cashins amp Associates Inc of Reading MA performed the following work as a subcontractor to TFCI
1) Preparation of a site-specific Health and Safety Plan (dated September 1 1995)
2) Provide a Field TechnicianIndustrial Hygienist to serve as Site Safety and Health Officer (SSHO) and to conduct air and noise monitoring
3) Provide a Certified Industrial Hygienist to review Health and Safety and to conduct site specific training (record of training included at end of Appendix C)
4) Collect 8-hour air samples for worker exposure and ambient air at the Barcelona Avenue gate Arrange for analysis of the samples and report results
5) Prepare daily and weekly Health and Safety reports
6) Prepare a Health and Safety Phase-Out Report
In general the following health and safety practices were followed
1) All workers wore hard hats safety glasses work boots gloves and hearing protection as minimum level PPE
2) When working in the exclusion zone workers wore in addition to above tyvek rubber overboots and rubber coated gloves When dust was a potential concern an industrial grade dustmist mask was also worn This level of PPE was considered Level D modified
3) Workers leaving the exclusion zone removed PPE (tyveks gloves boots and masks) in the support zone and either disposed of the items or decontaminated them
4) Workers andor visitors without 40-hour OSHA training were not permitted to enter the exclusion zone
Attached is a report prepared by Cashins amp Associates along with weekly Health and Safety Summary Reports prepared by the Field Hygienist In summary the air monitoring results indicate no levels exceeding the applicable exposure guidelines except one instance
During excavation of contaminated overburden in the northwest comer of the site an area of VOC contaminated soil was encountered Total VOCs levels measured using a PID exceeded the action level established in the Health and Safety Plan The SSHO advised TFCI to upgrade to Level C PPE in order to backfill the excavation in this area TFCI equipment operator upgraded and backfilled the area The SSHO in consultation with the Cashins CIH advised TFCI to avoid work in this area until the contaminants were characterized GEI sampled the material for waste characterization analysis and provided the results to TFCI Based on the results an action level was established by the CIH for the specific contaminants found Further PID measurements indicated levels below the new action level and work was resumed
The noise monitoring indicated that the noise level at the Barcelona Avenue gate was not exceeded Only one instance of excess noise level in the work zone was recorded (10 db(a) above the ambient noise level or 85 db(a)) Workers wore hearing protection in this instance
mdash 07171996 1601 6179444032 CASHIMS S ASSOCIATES PAGE 02
CASHINS amp Associates Inc
ItxhalrM Hy-gifnr A Invtronmtnltl Tttling
July 17 1996
Mr Jack Enos T Ford Company Inc USTenney Street Georgetown MA 01833
Dear Jack
The Site Safety and Health Officer (SSHO) from Cashing amp Associates Inc performed daily inspections of the SL-4 area Salem Acres Superfund Site between 9595 and 12195 in accordance with the Health amp Safety Plan (HSP) for the site Daily inspection logs were submitted every day No accidentsincidents were reported during the work period
In accordance with the Health amp Safety Plan the SSHO performed daily air and noise monitoring at the site during Ac project Samples were collected for metals (lead beryllium chromium arsenic) and Polynuclear Aromatic Hydrocarbons (PAHs) at the site perimeter and for workers exposure determination Coal Tar Pitch Volatiles (a benzene soluble extractables) were also used to determine the workers exposure to PAH compounds Coal Tar Pitch Volatiles (CTPV) were analyzed using OSHA 58 Method If CTPV levels oq personal samples exceed the site criteria of 02 ragm3 the sample was submitted for PAHs analysis All air samples on the site perimeter were analyzed for PAH compounds
Site monitoring air sample collection and results report were done under the supervision of a Certified Industrial Hygienist
Full shift personal worker exposure samples were collected once a week Ambient air samples were collected at the Barcelona Avenue gate about 20 feet to the west of the site gate to determine if site contaminants were migrating off site The ambient air samples were also collected once a week during the project except on rainy days and days without work with contaminated soil
All air samples were analyzed by the American Industrial Hygiene Association accredited ESA Laboratories Inc using the following methods PAHs - NIOSH 5515 Lead - NIOSH 7082 Beryllium - NIOSH 7102 Chromium - NIOSH 7024 Arsenic - NIOSH 7900 Coal Tar Pitch Volatiles - OSHA 58 All methods used are accepted by the industrial hygiene community for 8-hour exposure assessment EPA methods are usually used for ambient air measurements
CRErORTTFOmiOO
80 Mam Street bull Reading MA 01867 bull Phone- 61 7-944-4060 bull Fax 61 7-944-4082
07171996 1601 6179444032 CASHIMS amp ASSOCIATES PAGE 03
The results of air samples for metals and PAHs are presented in Table No 1
All concentrations of metals and PAHs at the site perimeter (Barcelona Avenue) and active work zones were below the OSHA Permissible Exposure Limits (PEL) and the American Conference of Governmental Industrial Hygicnists Threshold Limit Value (ACGIH TLV) Two personal samples collected on October 19 and October 23rd showed Coal Tar Pitch Volatiles (CTPV) results above OSHA PEL and AIHA TLV limits Both samples were resubmittcd to the lab for further analysis to determine if PAH compounds are present because the CTPV results were above site criteria
The results of the PAH concentrations for the personal sample on Mark Goodwin on October 19 1995 during excavation and washing trucks and for the personal sample on Ron Maker on October 23 1995 during excavating and cleaning rocks by compressed air were below OSHA PEL and ACGIH TLV limits
The SSHO performed noise monitoring according to the HSP at the exclusion zone and at the Barcelona Avenue site perimeter fence A Dupont sound level meter was used for noise monitoring The noise level in the exclusion zone during all operations except one did not exceed the on site criteria of 85 dB(a) During a short time when the air compressor had been used to clean rocks the sound level in the exclusion zone next to the air compressor did exceed 85 dB(a) Ear protection devices were worn by the workers during that operation At no time did the noise level at the Barcelona Avenue site perimeter exceed 10 dB(a) above the ambient noise level or 85 dB(a)
The SSHO performed total dust monitoring on a daily basis during the project at the site perimeter downwind of work location and at the site gate using a Miniram real time dust meter The summary of dust monitoring is presented in Table No 2 Total dust concentrations on site and off site did not exceed site criteria of 1 mgm3 and the action level of 05 nigny1
The summary of air monitoring for Volatile Organic Compounds (VOC) is presented in Table No 3 VOC concentrations in the working area did not exceed the on site criteria of 5 ppm in a breathing zone VOC concentrations on the site perimeter did not exceed real time off site criteria of 2 ppm
Five detail reports with results of air sampling were submitted during the project period
Sincerely Cashins amp Associates Inc
Evelina Vaughan Industrial Hygieflfst
CASHINS amp ASSOCIATES Inc
80 Mam Street bull Reading MA 01867 bull Phone61 7-944-4060 bull Fax 617-944-4082
07171996 1601 6179444082 CASHINS S ASSOCIATES PAGE 04
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80 Main Street Reading MA 01867 bull Phone617-944-4060 bull Fax617-944-4082
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80 Main Street bull Reading MA 01867 bull Phone617-944-4060 bull Fax617-944-4082
CASHINS amp Associates Inc
Industrial Hygiene amp Environmental Testing
SITE SPECIFIC amp HAZARD COMMUNICATIONS TRAINING SIGN-IN SHEET
ftt poundpoundpound
DATE
LOCATION OF TRAINING $ALt_M ACu
TIME 9 ^ rW
NAME COMPANY SIGNATURE
40 SALEM ST bull LYNNFIELD MA 011J40 bull TEL 617-2-)5-J77J - FAX ()l7-MS-tUrj
OSHINSamp Associates Inc
Industrill Hygiene amp Environnivnljl fating
SITE SPECIFIC amp HAZARD COMMUNICATIONS TRAINING SIGN-IN SHEET
DATE poundLOCATION OF TRAINING
TIME
NAME COMPANY SIGNATURE
j
40 SAUM ST bull LYNNFIELD MA (J1J40 bull TEL 617-2-T 1773 FAX (gtI7 M5-iU7i
CASHINS amp Associates Inc
Industrie Hygitmt amp tnvironmvnlal
SITE SPECIFIC amp HAZARD COMMUNICATIONS TRAINING SIGN-IN SHEET
DATE
LOCATION OF TRAINING
ir bull vr~ TIME - laquo t bullgt
NAME COMPANY SIGNATURE
r_
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40 SALEM ST bull LYNNFIELD MA 01J40 bull TEL 617-245-J77J bull FAX (gtl7--IS4()rj
89111995 1023 6172733(384 CASHINS ASSOCIATES PAGE 01
CASHINS amp Associates inc
Ifxtuitral Hygltne A fnvironmtnltt Tuning
W3SXLY HBALTH amp SAFETY PLAN COMPLIANCE SUMMARY R3PORT
CLIENT T foyd C o m a n
LOCATION gal era Acres Sx^perfund Site 8L-4 Area
DATES INCLUDED IN SUMMARY
toe
-
SUMMARIZED BY FOR CASHINS amp ASSOCIATES INC
55 CAMBRIDGE STREET bull SUITE 201 bull BURLINGTON MA 01803 laquo TEL 61 -273-9080 bull FAX 67-273-9C84
09111995 1023 6172739084 CASHINS ASSOCIATES PAGE 01
CASHINSamp Associates Inc
Induttrml Hygttnr t Emtroomtnttl Ttstinf
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Fprd Company
LOCATION Salen Acres Suoerfund Site SL-4 Area
DATES INCLUDED IN SUMMARY
000 mdash0
ITr-
^ tcf f
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SUMMARIZED BY FOR CASHINS 4 ASSOCIATES INC
55 CAMBRIDGE STREET bull SUITE 201 bull BURLINGTON MA 01803 raquo- TEL 6J 7-273-9080 bull FAX 617-273-9084
CASHINS amp Associates Inc
Industrial Hygitnf amp CmimnmenUl Tinting
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Compan
LOCATION Salem Acres Superfund Site SL-4 Area
DATES INCLUDED IN SUMMARY
-amp
I
tu bull lts fffr-t TC mdash
bull amppoundf-te
-ampp
4 shy
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SUMMARIZED BY FOR CASHINS amp ASSOCIATES INC
55 CAMBRIDGE STREET SUTE20 bull BLRLINCTON MA 01803 TEL-b l 7-273-9080 bull FAX 61 r-~3-084
CASHING X ASSOCIATES PAGE
1C n -044408shy07161336 1650 61 344408shy
CASHINSamp Associates Inc
WEEKLY HEALTH amp SAFBTT PLAN COMPLIANCE SUMMARY REPORT
CLIENT ^T Ford Combanv
LOCATION Salam Aerag SL-4
DATES INCLUDED IN SUMMARY
- ^ ^
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55 CAMBRIDGE STREET bull SUITE 201 bull SURUNCTON vu 01803 TEL 61 rori-^oao FAX 61 ~ rj
07161996 1650 6179444082 CASHI MS amp ASSOCIATES PAGE 10
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DATES INCLUDED IN BUNKARY)
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55 CAM8RJDCpound STWET bull SUTTE201 eolaquolNCTONMAOJlaquo03 TIL 6t7shy
07161996 1650 6179444082 CASH INS amp ASSOCIATES PAGE 08
CASHINSamp Associates Inc
Intutttitl Myffcnt t InvtmnmmUt Itnl
WEEKLY HEALTH 6 SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Fortjl Cqjapany
LOCATION Salem Acrlaquoa Superfund Site 9L-4 Area
DATES INCLUDED IN SUMMARY
s
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ampspounde
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55 CAMBRIDGE STREFT SUITE 201 bull BURUNCTON MA oisoa bull TEL 617-273-9030 bull FAX 6i 7-273-9084
77
OSHINSamp Associates Inc
Industrial Hygiene amp Emironmvntal Testing
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Company
LOCATION Salem Acres Superfund Site SL-4 Area
DATES INCLUDED IN SUMMARY J_
pound0
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5 CAMBRIDGE STREET bull SUITE JO I bull BURLINGTON MA 01 K03 TEL ltjl 7-J7J-9080 bull FAX b I 7-273-9084
CASHINS amp Associates Inc
Industrial Hygifnr amp [nvironmenljl res
SERIOUS HAZARD NOTIFICATION
ISSUED TO REPRESENTING
ISSUED BY REPRESENTING CASHINS S ASSOCIATES INcT DAY DATE ISSUED O04Xmdash 1 bull-bullmdashbull f P^JT
PROJECT NAME_ SITE LOCATION
THE PURPOSE OF THE FOLLOWING STATEMENT IS TO DOCUMENT THE EXISTENCE OF A CONDITION OR CONCERN WHICH CASHINS amp ASSOCIATES INC BELIEVES WARRANTS IMMEDIATE CORRECTIVE ACTION POSSIBLE SOLUTIONS AND OR CORRECTIVE ACTIONS WILL BE INCLUDED IN THIS NOTIFICATION WHEN POSSIBLE THIS NOTIFICATION IS LIMITED TO SITUATIONS THAT REPRESENT EITHER IMMEDIATE DANGER TO LIFE OR HEALTH CONDITIONS OR PREVIOUSLY IDENTIFIED CHRONIC PROBLEMS THAT UNDERMINE OUR ABILITY TO EFFECTIVELY INSURE COMPLIANCE WITH THE REQUIREMENTS OF THE HEALTH AND SAFETY PLAN
0
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55 CAMBRIDGE STREET bull SUITE 201 bull BURLINGTON MA 01 803 bull TEL 61 7-273-9080 bull FAX fgtl 7-273-9084
CISHINS amp Associates Inc
Industrial Hygirne amp Cmimnmtntal Testing
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Company
LOCATION Salem Acres Superfund Site SL-4 Area
DATES INCLUDED IN SUMMARY T
(5 f0^ degT a
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SUMMARIZED BY FOR CASHINS amp ASSOCIATES INC
f a 7 ) ) F A X i gt I 7-273-^)84
87161996 1650 6179444882 CASHINS amp ASSOCIATES
CASHINSamp Associates Inc
WEEKLY HEALTH amp SA7STT PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Coqpanv
LOCATION Sa^am Acras Super fund 5 jte SL-4 Area
DATES INCLUDED IN SUMMARY bull
11 bdquo mdashbull - ampruzpoundtC4 poundLampu ^6zUT
b( I fa We
FOR CASHINS amp ASSOCIATES INC
53 CAMBRIDGE STREET bull SUTE40I bull BURIJSCTON MA 0803 TfL 61 7-273-908O bull FAX fairo-Jshy
07161996 1658 6179444032 CASHINS S ASSOCIATES PAGE 86
CASHINSamp Associates Inc
MtanW HriHtif A
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT ^ mdash
CLIENT T Ford Company
LOCATION Salem Acraa Suoerfund Sita 5L-4
DATES INCLUDED IN SUMMARY bull
6 03 HL fro- TH4-shy
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fo
SUMMARIZED BY FOR CASHINS amp ASSOCIATES INC
55 CAMBRIDGE STREET bullSUITE 201 bull BURllNCTON MA 01803 bull TEL 617-273-9080 bull FAX 617-273-9084
07161996 1650 617944408 CASHING 3 ASSOCIATES PAGE 05
CASHINSamp Associates Inc
fmimnntattl few
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT t T Ford Coimbanv
LOCATION t Salam Acraa Suoarfund Site SL-4 Arlaquoa
DATES INCLUDED IN SUMMARYj pound mdashiffofrshy f
K (J
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SUMMARIZ2D BY _ ampampS FOR CASHINS amp ASSOCIATES INC
55 CAMBRIDGE STREET bull SUITE 201 bull BURLINGTON MA 01803 lt TEL 617-273-9080 bull FAX 617-273-9084
CASHIMS amp ASSOCIATES PAGE 04 07161996 1658 6179444032
OVSHINSamp Associates Inc
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Company T
LOCATION Salem AcrM Suoerfund Stta 8L-4 Araa
DATES INCLUDED IN SUMMARY
(7
ft ^ 0
SUMMARIZED BY pound FOR CASHINS amp ASSOCIATES INC
55 CAMBRIDGE STREET bull SUITE 201 bull BURUNGTON MA 01803 bull TEL 617-273-9080 bull FAX 617-273-9084
07161996 1658 6179444082 CASHIMS 3 ASSOCIATES PAGE 03
CASHINSamp Associates Inc
ndurtrW Hrtnm t
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT ^
CLIENT T Ford Company t lP ~ ff2-r
LOCATION Sal era Acraa Suplaquorfund Sj-ta 8L-4 Araa
DATES INCLUDED IN SUMMARY
if
j
(J
SUMMARIZED BY FOR CASMINS amp ASSOCIATES INC
55 CAMBRIDGE STREET bull SUITE 201 bull 8URUNGTON MA 01803 bull TEL 617-273-9080 bull FAX 617-273-90W
07151996 18 fO 6179444082 CASHINS S ASSOCIATES PAGE 02
CASHINS amp Associates Inc
WBBKLY HEALTH amp SAFETY FLAK COMPLIANCE SUMMARY REPORT
CLIENT T Ford Compapv
LOCATION i Sal am Acrlaquolaquo Suparfund Sita SL-4 Area
DATES INCLUDED IN SUMMARY i bull pound7 mdash
A 0-3 - A)
SXWMARIZ2D BY FOR CASHINS amp ASSOCIATES INC (
55 CAMBRIDGE STREET SUITE 201 bull SURtlNCTON MA 01803 TEL 617-273-9080 bull FAX 61 7-273-9084
- barcode 14732
- barcodetext SEMS Doc ID 14732
![Page 11: SALEM ACRES SUPERFUND SITE SALEM, MA ...The truck loading pa d consisted of a crushed stone are sea t up along the east sid e o f SL-4 adjacent to the access road A. row of concrete](https://reader036.vdocuments.us/reader036/viewer/2022070114/60729b840fec4e6b4d136a16/html5/thumbnails/11.jpg)
Moran surveys because the material was in or under active stockpiles at the time of the survey The quantity survey and method of calculation is described in a letter from T F Moran dated January 15 1996 and contained in Appendix B
42 Limits of Remediation
In order to document the limits of remediation T F Moran surveyed the site on November 1 and December 5 1995 Areas where contaminated overburden were removed were surveyed at these times including the limits of exposed bedrock The results of these surveys are shown on Figure 4 The limits of SL-4 site remediation are as follows
Total Site Area Remediated 50860 sf Exposed Ledge 19990 sf
Site Restoration Area 30870 sf
In addition Area 1 is approximately 5416 sf
Note that the total quantity of contaminated overburden and fly ashsoildebris mixture was 6056 tons compared to the estimated 4100 tons from the design studies The primary reasons for the increase include the following
Incorporation of Area 1 from SL-5 in the SL-4 site remediation work
The northern limit of excavation extended further into DA-1 than anticipated in the RA Work Plan
Excavating further west into WA-1 than anticipated in the RA Work Plan
VOC contaminated fly ash and soil in the northwest corner near DAshy1 at a considerable thicknessdepth
The limits of remediation survey are described in the T F Moran letter contained in Appendix B
43 Final As-Built
A final as-built survey was performed by T F Moran on May 21 1996 The results of the survey are shown on Figure 5
TABLE 1 SUMMARY OF ASH REMOVAL
SALEM ACRES SUPERFUND SITE SL-4 AREA
DATE NOMBEraquo0poundLOADS
0AILY TOTAL ifrotfS) i
SEPTS 1 1750
SEPT 1 1 8 13470
SEPT 12 10 21080
SEPT 13 20 45800
SEPT 14 23 50100
SEPT 15 20 43160
SEPT 18 23 46870
SEPT 19 24 54780
SEPT 20 26 52800
SEPT 21 25 47700
SEPT 22 25 46915
SEPT 25 26 51950
SEPT 26 29 56820
SEPT 27 30 55660
SEPT 28 30 58410
SEPT 29 26 53520
OCT2 26 54600
OCT3 26 57000
OCT4 19 41080
OCT5 22 49240
OCT6 26 61860
OCT 10 18 47180
OCT 11 12 33860
OCT 13 17 439 40
OCT 17 3 7600
OCT 19 3 7720
CtnVfOtATIVE TOTAL (TONS)
1750
15220
36300
82100
132200
175360
222230
277010
329810
3775 10
424425
476375
5331 95
5888 55
647265
700785
755385
812385
853465
902705
9645 65
1011745
1045605
1089545
1097145
1104865
TABLE 2 SUMMARY OF CONTAMINATED
OVERBURDEN REMOVAL SALEM ACRES SUPERFUND SITE SL-4 AREA
DATE
on 19 OCT 20
OCT 23
OCT 24
OCT 25
OCT 26
OCT 27
OCT 31
NOV 1
NOV2
NOV 6
NOV 8
NOV 9
NOV 21
NOV 28
DEC 7
NUMBER OF LOADS
14
14
14
13
14
16
18
18
12
4
4
8
8
8
9
2
DAILY TOTAL (TONS)
46121
41649
49314
448 59
46225
48054
62358
56186
491 56
14209
14025
29010
27604
35513
33447
7885
CUMULATIVE TOTAL (TONS)
46121
87770
137084
181943
228168
276222
338580
394766
443922
458131
472156
501166
528770
564283
597730
6056 1 5
- -
--
Oct 17 1995 823PM P02 From LTTS OF Mfl INC PHONE No 617 438 S21S
GRftIN SIZE DISTRIBUTION TEST REPORT C c c e
100 i i ^ i i 7 ^ d bdquo bdquo j laquo ii i A j
bdquo9 bdquo
a 2 - a i
t sh
90 X
N^
B0 raquo m lts
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70 Sk
gtia
Npound G0 shyu
550 gt
UJ bullshy
1u S pound 40 0 ^
30 bull i 20
10
0 2Q 0 1SG 100 10 01 aai 00UL
CRflIM CISC - mm
Test X +3 bull4 GRAVEL bull SflMD bull SILT bull DRY uses LL PI
t 16 00 2Z 3 521 256 SC-SM
SIEVE PERCENT FINCR STEVE PERCENT FINCR Uact on Incrwi nuwtoer ilz ilzi bull flUNSON ST PEABODC
bull bull a 96 3 4 777
15 95 10 714 1 92 e 20 607 Descr pt ion
075 90 40 505 bullSILTY CLAYEY GflNO 0 375 34 50 44 4
100 343
3X1 GRAIN SIZE 200 257
8804D60
gtDia Remarks
xC COEFh 1C1CNT5 UTS OF MASSACHUSETTS INC bull
SS1T to 1 u
Pro jlt-r t No UTS OF naSSACHLKKI lgt IMC Project) CftLCM flCHSCC
5 Richardson Lane
GtoneHam Mft 03 IBB Date 101195 Gamn 1 c- No 44fi1A
Figure 1
From UTS OF Mfl INC PHONE No 517 438 6216 Oct 17 1995 824PM F03
SOT ANALYSIS REPORT FOR NEW LAWN 101195
SOIL AND PLANT TISSUE TESTING LABWEST EXPERIMENT STATIONUNIVERSITY OF MASBACIIUfiFTTr AMHERST MA 01003
LAB NUMBER 3951010-107 BAG NUMBER 23467
DATE BFNT f
SOIL FROM COUNTY SOIL WEIGHT 537 g5cn CROP TURFORASS
UTS OF MASS INC COMMENTS ORGANIC MATTER 6 RICHARDSON LANE STONEHAM MA 02180
SAMPLE ID 4461B
LIMESTONE AND FERTILIZER RECOMMCNDATIONS FOR NEW LAWN CONSTRUCTION
No limestone ia required If peat mooc or similar material ia to be incorporated) see enclosed fact sheet
Fertilizer (per 10OO sq ft) 2 1ba N 2 Ibo P2O5 and O 1 bs KZO
Many fertilizer sources and rates may combine to provide acceptable turfgraes establ iahmont either from seed or aod One or two options baaed on this soil teat follow
Incorporate EITHER a 17-23-6 starter fert111zar at 10 lbs1000 sq ft OR a 30-3-3 lawn fertilizer at 7 1b81000 aq ft plus a 0-45-0 (triple superphosphate) fertilizer at 4 lbs1000 aq ft Hnto the top 3 to 4 inches of soil Retest Bull ona year after turf establishment
PLEASE read the enclosed fact sheets for niora specific Information on fertilization and liming procadurea
SOIL pH 71 NITROGEN NO3-N = Oa ppm NH4-N = 5 ppm BUFFER pH 74 ORGANIC MATTER 72 X (Desirable range 4-10X)
NUTRIENT_LEVELS_PPM_| Low Medium High Very High Phosphorus (P) 8 |XXXXXXXXXXXXX Potaaaium (K) 292 [XXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXX Calcium (Ca) 237S XXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXX Magnesium (Mg) 237 JXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXX
CATION EXCII CAP PERCENT BASE SATURATION MICRONUTRIENT LEVELS 130 Meq100g K= 52 Mg=134 Ca=816 ALL NORMAL
CXTRACTABLE ALUMINUM 41 ppm (Soil ranglaquo 10-250 ppm)
The lead level in thio soil 1s low
COMPUTER PROGRAM5-RECOMMENDATIONRbYOtHIOFPtANT~ampSOILSCI UMASS-AMHERST
Figure 2
TARGET SHEET
THE MATERIAL DESCRIBED BELOW WAS NOT SCANNED BECAUSE
(X) OVERSIZED
() NON-PAPER MEDIA
() OTHER
DESCRIPTION DOC 14732 DRAFT FINAL REMEDIAL CONSTRUCTION REPORT FIGURE 3 TOPOGRAPHIC PLAN SL-4 AREA BOTTOM OF FLY ASH SALEM ACRES SHEET 1 OF 1
THE OMITTED MATERIAL IS AVAILABLE FOR REVIEW BY APPOINTMENT
AT THE EPA NEW ENGLAND SUPERFUND RECORDS CENTER BOSTON MA
TARGET SHEET
THE MATERIAL DESCRIBED BELOW WAS NOT SCANNED BECAUSE
(X) OVERSIZED
() NON-PAPER MEDIA
() OTHER
DESCRIPTION DOC 14732 DRAFT FINAL REMEDIAL CONSTRUCTION REPORT FIGURE 4 TOPOGRAPHIC PLAN SL-4 AREA LIMIT OF REMEDIATION SALEM ACRES SHEET 1OF1
THE OMITTED MATERIAL IS AVAILABLE FOR REVIEW BY APPOINTMENT
AT THE EPA NEW ENGLAND SUPERFUND RECORDS CENTER BOSTON MA
TARGET SHEET
THE MATERIAL DESCRIBED BELOW WAS NOT SCANNED BECAUSE
(X) OVERSIZED
() NON-PAPER MEDIA
() OTHER
DESCRIPTION DOC 14732 DRAFT FINAL REMEDIAL CONSTRUCTION REPORT FIGURE 5 TOPOGRAPHIC PLAN SL-4 AREA AS-BUILT PLAN SALEM ACRES SHEET 1 OF 1
THE OMITTED MATERIAL IS AVAILABLE FOR REVIEW BY APPOINTMENT
AT THE EPA NEW ENGLAND SUPERFUND RECORDS CENTER BOSTON MA
(i)
^mft^m
VIEW OF BARCELONA AVENUE THROUGH ENTRANCE GATE PRECONT RUCTION
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(2)
VIEW OF ACCESS ROAD LOOKING NORTH SL-4 ON LEFT PRECONSTRUCTION
VIEW OF ACCESS ROAD LOOKING NORTH SL-4 ON LEFT DA-1 TO LEFT OF PICKUP TRUCK
PRECONSTRUCTION
(3)
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
O ID a CO z O OHI
CO UJ
OO_l
t CO ii-O
(5)
VIEW OF BOUNDARY BETWEEN SL-4 AND DA-1 LOOKING WEST PRECONSTRUCTION
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(6)
EROSION CONTROLS LOOKING NORTH FROM CORNER OF SL-4SL-5 ADJACENT TO WA-1 PRECONSTRUCTION
(7)
TRUCK LOADING PAD LOOKING NORTHWEST FROM SUPPORT ZONE
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(8)
DECONTAMINATION PAD LOOKING NORTHWEST FROM SUPPORT ZONE
(9)
EXCAVATION OF FLY ASH LOOKING NORTHWEST FROM CRZ NOTE WATER FOR DUST CONTROL
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(10)
VIEW LOOKING WEST AFTER REMOVAL OF FLY ASH NOTE WA-1 BEYOND EROSION CONTROLS
(11)
EXCAVATION OF CONTAMINATED OVERBURDEN LOOKING SOUTH FROM DA-1 BOUNDARY
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(12)
VIEW OF RESTORED SITE LOOKING WEST TOWARD WA-1
0
ltu
wsectbull
D Q
O
O z ^ O O_J LJJ
Q LJJ a o te LJJ
eg 3
(14)
VIEW OF RESTORED SITE LOOKING NORTH TOWARD DA-1 ALONG ACCESS ROAD
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(15)
gtbull bdquobdquo -
VIEW OF RESTORED SITE LOOKING SOUTH TOWARD SL-5
iu O
of bullo
01 u I ltO
w
o B ltabulls to 10
3
I Q Z
O m ^mdash
i sect^^ nu0 (- co^gtW IO - z zilaquo O O 5gl
oLU uj
V) LUo a o LU
(17)
VIEW OF RESTORED SITE ON DA-1 SJDE OF FENCE - LOOKING ST
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(18)
VIEW OF RESTORED SITE ON DA-1 SIDE OF FENCE - LOOKING WEST SL-4 ON RIGHT
APPENDIX A
ANALYTICAL RESULTS FOR
PONDED WATER
110795 1638 copy617 890 3883 TMA-WALTHAM ] 002007
PRELIMINARY REPORT UNAUDITED RESULTS
Thenno Analytical 300 Second Avenue PO Box 521 Waltham HA 02254
Attn Client Services Phone (617) 890-7200
Cashins amp Associates Order S5-11-034 55 Cambridge Street Date 110795 1522 Burlington HA 01803 Work ID Salem Acres Water
Date Received 110295 Attn Bob Cashins Date Completed
Purchase Order NA Invoice Number Client Code CASHINS
SAMPLE IDENTIFICATION
Sample Sample Number Description 01 11019S-924-01A
Sample Number 04
Sample Description
110195-9Z4-01D 02 110195-924-01B 05 110195-924-01E 03 110195-924-01C
Certified By
110795 1638 copy617 890 3883 TMA-WALTHAM 003007
PRELIMINARY REPORT UNAUDITED RESULTS
Order f S5-11-034 Thermo Analytical Page 2 110795 1522 TEST RESULTS BY SAHPLE
Test Description Volatile Organics- Aqueous Method EPA_8240 Test Code Collected 110195 02-00 Category WATER
DATE INJECTED 110695 DILUTION FACTOR 100 All results reported 1n ugL
COMPOUND RESULT DET LIMIT COMPOUND RESULT
Chloromethane U 10 Broroodi chl oromethane U Vinyl Chloride U 10 2-Chloroethyl Vinyl Ether U
Bromxnethane U 10 4-dethyl -2-pentanone U Chloroethane U 10 c1 3-1 3-Di chl oropropene U
Trichlorofluoronwthane U 50 Tol uene U Acetone 17 10 trans-1 3-Di chl oropropene LI
11-Oichloroethene U 50 11 2-Tri chl oroethane J Carbon Dlsulfide U 50 2-Hexanone U
Methyl ene Chloride U 50 Tetrachl oroethene U 12-Oichloroethene (total) U 50 D1 bromochl oromethane U
11-01 Chloroethane U 50 Chlorobenzene U Vinyl Acetate U 10 Ethyl benzene U
2-Butanone U 10 in and p-Xylene U Chloroform U 50 o-Xylene U
111-Tri Chloroethane U 50 Styrene U Carbon Tetrachlortde U 50 Broraoform U
Benzene U 50 112 2-Tat rachl oroethane U 12-01 Chloroethane U 50 1 3-01 chl orobenzene U
Trichloroethene U 50 I 4-Di chl orobenzene U 12-Dichloropropane U 50 12-01 chl orobenzene U
SURROGATE STANDARDS RESULT LEVEL X RECOVERY
12-Dichloroethane-D4 52 50 104 Toluene-08 47 50 94
l-Bromo-4-fluorobenzene 56 50 112
NOTES AND DEFINITIONS FOR THIS REPORT U =bull Undetected at stated detection limit
VOAJI
OET LIMIT
50 50
10 50 50 50 50 10
5 0 50 5 0 5 0 50 50 50 50 50 50 50 50
110795 1639 copy617 890 3883 TMA-WALTHAM copy004007
PRELIMINARY REPORT UNAUDITED RESULTS
Order t S5-11-034 Thermo Analytical Page 4 110795 1522 TEST RESULTS BY SAMPLE
ianple Description 110195-924-010 Lab No 04A Test Description RCRA Metals 1n Water Method SW846 Test Code
Collected 110195 0200 Category WATER
METAL RESULT DETECTION LIMIT METAL RESULT DETECTION LIMIT
Ag Silver U 10 As Arsenic 870 50
Ba Bar inn B69 10 Pb Lead U 50
Cd Cadmium U 50 Se Sel en1 um Z15 50
Cr Chromi um U 20 Hg Mercury U 020
NOTES AND DEFINITIONS FOR THIS REPORT All results reported in ugL U gt Undetected at stated detection limit
110795 1640 Q617 890 3883 TMA-WALTHAM 0005007
PRELIMINARY REPORT UNAUDITED RESULTS
Order S5-11-034 Thermo Analytical Page 5 110795 1522 REGULAR TEST RESULTS BY TEST
Chemical Oxygen Demand Mlnimun Maximum Method EPA600 4101
Sap Sample Description Result Units Limit Prepared Analyzed By 05A 110195-924-01E 64 bullgL 50 110395 110395 JD
Petroleum Hydrocarbons-H20 Minimum Maximum Method EPA600 4181
Samp Sample Description Result Units Limit Prepared Analyzed By 01A 110195-924-01A 108 mgL 050 110395 110395 JO
110795 1640 reg617 890 3883 TMA-WALTHAM copy006007
PRELIMINARY REPORT UNAUDITED RESULTS
Order I S5-11-034 Therm Analytical Page 6 110795 1522 TEST METHODOLOGIES
USEPA Test Methods for Evaluating Solid Wastes (SUS46 Third Edition) Method 7470 - Preparation of water for Mercury analysis
USEPA Test Methods for Evaluating Solid Vastes (SW846 Third Edition) Method 3010 - Add digestion of aqueous samples and extracts for total metals for analysis by Flame Atomic Absorption Spectroscopy or Inductively Coupled Plasma Spectroscopy
USEPA Test Methods for Evaluating Solid Vastes (SWB46 Third Edition Method 8270 mdash Gas ChroroatographyMass Spectrometry for PAHs
Volatile Organics in Water - Hazardous Substance List
SV846 Method 8240 - Modified
Test Methods for Evaluating Solid Waste SU-846 US EPA Office of Solid Waste and Emergency Response Washington 3rd Edition
Aqueous sanples are analyzed in accordance with Method 8240 using a purge and trap technique followed by 64s ChromatographyMass Spectroscopy
Quality assurance procedures for GCMS Include daily tuning and calibration of the mass spectrometer and the use of surrogate standards in each sample to monitor method performance Quantitatton is performed by the Internal standard method Analysis of blanks duplicate samples and standards are run frequently as further quality assurance procedures
USEPA Test Methods for Evaluating Solid Wastes (SW846 Third Edition) Method 3S10 mdash Separatory Funnel Liquid-Liquid Extraction
EPA-6004-79-020 - Chemical Oxygen Demand - Titrimetric Mid-Level Method 4101
EPA6004-79-020 - Petroleum Hydrocarbons 1n Water Total Recoverable Method 4181 (Spectrophotometric Infrared)
110795 1641 copy617 890 3883 TMA-WALTHAM copy007007
APPENDIX B
QUANTITY SURVEY DOCUMENTATION
TFMORAN INC Surveying - Engineering - Land Planning SoilsWetlands Mapping - Landscape Architecture
January 15 1996
Mr Jack Enos Vice President TFord Company Inc 118 Tenney Street Georgetown MA 01833
RE Survey Results - Salem Acres - SL4 Area Salem Massachusetts
Dear Jack
This letter amends the letter of December 13 1995 per our review last week
TFMoran Inc performed topographic surveys at the Salem Acres site on April 21 1994 for GEI Consultants prior to removal of material and for TFord Company on October 18 1995 after the removal of material The survey data from the original survey in 1994 was adjusted thirty feet higher to correct for a datum difference from current site datum This was due to the original reporting of the Site Benchmark (TP34) elevation as 11464 rather than 14464 which is the correct elevation
Once both topographic surfaces were on the site datum the raw cut volume was obtained by Eaglepoint (Volumes Module) Software utilizing the prismoidal method comparing the two surfaces For reference please see the attached topographic plan which superimposes the October 15 1995 contours (dark lines) over the April 21 1994 contours The volume is based on the intersection of the two surfaces Also it was noted that stock piles of material did exist on site which were not surveyed at the time
The final raw cut volume arrived at by the above methods is 12749 Cubic Yards
In November and December of 1995 the site was resurveyed to locate the area of exposed ledge at the site The results of this survey are shown on the attached topographic worksheet dated November 3 1995 and last revised January 15 1996 The results of the survey indicate the total site area to be 50860 sq ft or 117 acres The total area of exposed ledge surveyed is 19990 sq ft or 46 acres If you have any questions regarding the above call me directly Thank you
Sincerely
John W Myhaver Jr ^_ Field Operations Manager
Enclosure ItorLltr
Route 101 Bedford NH 03110 Phone (603) 472-4488 FAX (603) 472-9747
APPENDIX C
HEALTH AND SAFETY PHASE-OUT REPORT
HEALTH AND SAFETY PHASE-OUT REPORT SALEM ACRES SL-4 AREA
Introduction
During remediation work on SL-4 Health and Safety Monitoring was performed Cashins amp Associates Inc of Reading MA performed the following work as a subcontractor to TFCI
1) Preparation of a site-specific Health and Safety Plan (dated September 1 1995)
2) Provide a Field TechnicianIndustrial Hygienist to serve as Site Safety and Health Officer (SSHO) and to conduct air and noise monitoring
3) Provide a Certified Industrial Hygienist to review Health and Safety and to conduct site specific training (record of training included at end of Appendix C)
4) Collect 8-hour air samples for worker exposure and ambient air at the Barcelona Avenue gate Arrange for analysis of the samples and report results
5) Prepare daily and weekly Health and Safety reports
6) Prepare a Health and Safety Phase-Out Report
In general the following health and safety practices were followed
1) All workers wore hard hats safety glasses work boots gloves and hearing protection as minimum level PPE
2) When working in the exclusion zone workers wore in addition to above tyvek rubber overboots and rubber coated gloves When dust was a potential concern an industrial grade dustmist mask was also worn This level of PPE was considered Level D modified
3) Workers leaving the exclusion zone removed PPE (tyveks gloves boots and masks) in the support zone and either disposed of the items or decontaminated them
4) Workers andor visitors without 40-hour OSHA training were not permitted to enter the exclusion zone
Attached is a report prepared by Cashins amp Associates along with weekly Health and Safety Summary Reports prepared by the Field Hygienist In summary the air monitoring results indicate no levels exceeding the applicable exposure guidelines except one instance
During excavation of contaminated overburden in the northwest comer of the site an area of VOC contaminated soil was encountered Total VOCs levels measured using a PID exceeded the action level established in the Health and Safety Plan The SSHO advised TFCI to upgrade to Level C PPE in order to backfill the excavation in this area TFCI equipment operator upgraded and backfilled the area The SSHO in consultation with the Cashins CIH advised TFCI to avoid work in this area until the contaminants were characterized GEI sampled the material for waste characterization analysis and provided the results to TFCI Based on the results an action level was established by the CIH for the specific contaminants found Further PID measurements indicated levels below the new action level and work was resumed
The noise monitoring indicated that the noise level at the Barcelona Avenue gate was not exceeded Only one instance of excess noise level in the work zone was recorded (10 db(a) above the ambient noise level or 85 db(a)) Workers wore hearing protection in this instance
mdash 07171996 1601 6179444032 CASHIMS S ASSOCIATES PAGE 02
CASHINS amp Associates Inc
ItxhalrM Hy-gifnr A Invtronmtnltl Tttling
July 17 1996
Mr Jack Enos T Ford Company Inc USTenney Street Georgetown MA 01833
Dear Jack
The Site Safety and Health Officer (SSHO) from Cashing amp Associates Inc performed daily inspections of the SL-4 area Salem Acres Superfund Site between 9595 and 12195 in accordance with the Health amp Safety Plan (HSP) for the site Daily inspection logs were submitted every day No accidentsincidents were reported during the work period
In accordance with the Health amp Safety Plan the SSHO performed daily air and noise monitoring at the site during Ac project Samples were collected for metals (lead beryllium chromium arsenic) and Polynuclear Aromatic Hydrocarbons (PAHs) at the site perimeter and for workers exposure determination Coal Tar Pitch Volatiles (a benzene soluble extractables) were also used to determine the workers exposure to PAH compounds Coal Tar Pitch Volatiles (CTPV) were analyzed using OSHA 58 Method If CTPV levels oq personal samples exceed the site criteria of 02 ragm3 the sample was submitted for PAHs analysis All air samples on the site perimeter were analyzed for PAH compounds
Site monitoring air sample collection and results report were done under the supervision of a Certified Industrial Hygienist
Full shift personal worker exposure samples were collected once a week Ambient air samples were collected at the Barcelona Avenue gate about 20 feet to the west of the site gate to determine if site contaminants were migrating off site The ambient air samples were also collected once a week during the project except on rainy days and days without work with contaminated soil
All air samples were analyzed by the American Industrial Hygiene Association accredited ESA Laboratories Inc using the following methods PAHs - NIOSH 5515 Lead - NIOSH 7082 Beryllium - NIOSH 7102 Chromium - NIOSH 7024 Arsenic - NIOSH 7900 Coal Tar Pitch Volatiles - OSHA 58 All methods used are accepted by the industrial hygiene community for 8-hour exposure assessment EPA methods are usually used for ambient air measurements
CRErORTTFOmiOO
80 Mam Street bull Reading MA 01867 bull Phone- 61 7-944-4060 bull Fax 61 7-944-4082
07171996 1601 6179444032 CASHIMS amp ASSOCIATES PAGE 03
The results of air samples for metals and PAHs are presented in Table No 1
All concentrations of metals and PAHs at the site perimeter (Barcelona Avenue) and active work zones were below the OSHA Permissible Exposure Limits (PEL) and the American Conference of Governmental Industrial Hygicnists Threshold Limit Value (ACGIH TLV) Two personal samples collected on October 19 and October 23rd showed Coal Tar Pitch Volatiles (CTPV) results above OSHA PEL and AIHA TLV limits Both samples were resubmittcd to the lab for further analysis to determine if PAH compounds are present because the CTPV results were above site criteria
The results of the PAH concentrations for the personal sample on Mark Goodwin on October 19 1995 during excavation and washing trucks and for the personal sample on Ron Maker on October 23 1995 during excavating and cleaning rocks by compressed air were below OSHA PEL and ACGIH TLV limits
The SSHO performed noise monitoring according to the HSP at the exclusion zone and at the Barcelona Avenue site perimeter fence A Dupont sound level meter was used for noise monitoring The noise level in the exclusion zone during all operations except one did not exceed the on site criteria of 85 dB(a) During a short time when the air compressor had been used to clean rocks the sound level in the exclusion zone next to the air compressor did exceed 85 dB(a) Ear protection devices were worn by the workers during that operation At no time did the noise level at the Barcelona Avenue site perimeter exceed 10 dB(a) above the ambient noise level or 85 dB(a)
The SSHO performed total dust monitoring on a daily basis during the project at the site perimeter downwind of work location and at the site gate using a Miniram real time dust meter The summary of dust monitoring is presented in Table No 2 Total dust concentrations on site and off site did not exceed site criteria of 1 mgm3 and the action level of 05 nigny1
The summary of air monitoring for Volatile Organic Compounds (VOC) is presented in Table No 3 VOC concentrations in the working area did not exceed the on site criteria of 5 ppm in a breathing zone VOC concentrations on the site perimeter did not exceed real time off site criteria of 2 ppm
Five detail reports with results of air sampling were submitted during the project period
Sincerely Cashins amp Associates Inc
Evelina Vaughan Industrial Hygieflfst
CASHINS amp ASSOCIATES Inc
80 Mam Street bull Reading MA 01867 bull Phone61 7-944-4060 bull Fax 617-944-4082
07171996 1601 6179444082 CASHINS S ASSOCIATES PAGE 04
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Ifxtuitral Hygltne A fnvironmtnltt Tuning
W3SXLY HBALTH amp SAFETY PLAN COMPLIANCE SUMMARY R3PORT
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LOCATION gal era Acres Sx^perfund Site 8L-4 Area
DATES INCLUDED IN SUMMARY
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LOCATION Salen Acres Suoerfund Site SL-4 Area
DATES INCLUDED IN SUMMARY
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Industrial Hygitnf amp CmimnmenUl Tinting
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
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LOCATION Salem Acres Superfund Site SL-4 Area
DATES INCLUDED IN SUMMARY
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LOCATION Salem Acres Superfund Site SL-4 Area
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LOCATION Salem Acres Superfund Site SL-4 Area
DATES INCLUDED IN SUMMARY T
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f a 7 ) ) F A X i gt I 7-273-^)84
87161996 1650 6179444882 CASHINS amp ASSOCIATES
CASHINSamp Associates Inc
WEEKLY HEALTH amp SA7STT PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Coqpanv
LOCATION Sa^am Acras Super fund 5 jte SL-4 Area
DATES INCLUDED IN SUMMARY bull
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07161996 1658 6179444032 CASHINS S ASSOCIATES PAGE 86
CASHINSamp Associates Inc
MtanW HriHtif A
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT ^ mdash
CLIENT T Ford Company
LOCATION Salem Acraa Suoerfund Sita 5L-4
DATES INCLUDED IN SUMMARY bull
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SUMMARIZED BY FOR CASHINS amp ASSOCIATES INC
55 CAMBRIDGE STREET bullSUITE 201 bull BURllNCTON MA 01803 bull TEL 617-273-9080 bull FAX 617-273-9084
07161996 1650 617944408 CASHING 3 ASSOCIATES PAGE 05
CASHINSamp Associates Inc
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WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT t T Ford Coimbanv
LOCATION t Salam Acraa Suoarfund Site SL-4 Arlaquoa
DATES INCLUDED IN SUMMARYj pound mdashiffofrshy f
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SUMMARIZ2D BY _ ampampS FOR CASHINS amp ASSOCIATES INC
55 CAMBRIDGE STREET bull SUITE 201 bull BURLINGTON MA 01803 lt TEL 617-273-9080 bull FAX 617-273-9084
CASHIMS amp ASSOCIATES PAGE 04 07161996 1658 6179444032
OVSHINSamp Associates Inc
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Company T
LOCATION Salem AcrM Suoerfund Stta 8L-4 Araa
DATES INCLUDED IN SUMMARY
(7
ft ^ 0
SUMMARIZED BY pound FOR CASHINS amp ASSOCIATES INC
55 CAMBRIDGE STREET bull SUITE 201 bull BURUNGTON MA 01803 bull TEL 617-273-9080 bull FAX 617-273-9084
07161996 1658 6179444082 CASHIMS 3 ASSOCIATES PAGE 03
CASHINSamp Associates Inc
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WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT ^
CLIENT T Ford Company t lP ~ ff2-r
LOCATION Sal era Acraa Suplaquorfund Sj-ta 8L-4 Araa
DATES INCLUDED IN SUMMARY
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SUMMARIZED BY FOR CASMINS amp ASSOCIATES INC
55 CAMBRIDGE STREET bull SUITE 201 bull 8URUNGTON MA 01803 bull TEL 617-273-9080 bull FAX 617-273-90W
07151996 18 fO 6179444082 CASHINS S ASSOCIATES PAGE 02
CASHINS amp Associates Inc
WBBKLY HEALTH amp SAFETY FLAK COMPLIANCE SUMMARY REPORT
CLIENT T Ford Compapv
LOCATION i Sal am Acrlaquolaquo Suparfund Sita SL-4 Area
DATES INCLUDED IN SUMMARY i bull pound7 mdash
A 0-3 - A)
SXWMARIZ2D BY FOR CASHINS amp ASSOCIATES INC (
55 CAMBRIDGE STREET SUITE 201 bull SURtlNCTON MA 01803 TEL 617-273-9080 bull FAX 61 7-273-9084
- barcode 14732
- barcodetext SEMS Doc ID 14732
![Page 12: SALEM ACRES SUPERFUND SITE SALEM, MA ...The truck loading pa d consisted of a crushed stone are sea t up along the east sid e o f SL-4 adjacent to the access road A. row of concrete](https://reader036.vdocuments.us/reader036/viewer/2022070114/60729b840fec4e6b4d136a16/html5/thumbnails/12.jpg)
TABLE 1 SUMMARY OF ASH REMOVAL
SALEM ACRES SUPERFUND SITE SL-4 AREA
DATE NOMBEraquo0poundLOADS
0AILY TOTAL ifrotfS) i
SEPTS 1 1750
SEPT 1 1 8 13470
SEPT 12 10 21080
SEPT 13 20 45800
SEPT 14 23 50100
SEPT 15 20 43160
SEPT 18 23 46870
SEPT 19 24 54780
SEPT 20 26 52800
SEPT 21 25 47700
SEPT 22 25 46915
SEPT 25 26 51950
SEPT 26 29 56820
SEPT 27 30 55660
SEPT 28 30 58410
SEPT 29 26 53520
OCT2 26 54600
OCT3 26 57000
OCT4 19 41080
OCT5 22 49240
OCT6 26 61860
OCT 10 18 47180
OCT 11 12 33860
OCT 13 17 439 40
OCT 17 3 7600
OCT 19 3 7720
CtnVfOtATIVE TOTAL (TONS)
1750
15220
36300
82100
132200
175360
222230
277010
329810
3775 10
424425
476375
5331 95
5888 55
647265
700785
755385
812385
853465
902705
9645 65
1011745
1045605
1089545
1097145
1104865
TABLE 2 SUMMARY OF CONTAMINATED
OVERBURDEN REMOVAL SALEM ACRES SUPERFUND SITE SL-4 AREA
DATE
on 19 OCT 20
OCT 23
OCT 24
OCT 25
OCT 26
OCT 27
OCT 31
NOV 1
NOV2
NOV 6
NOV 8
NOV 9
NOV 21
NOV 28
DEC 7
NUMBER OF LOADS
14
14
14
13
14
16
18
18
12
4
4
8
8
8
9
2
DAILY TOTAL (TONS)
46121
41649
49314
448 59
46225
48054
62358
56186
491 56
14209
14025
29010
27604
35513
33447
7885
CUMULATIVE TOTAL (TONS)
46121
87770
137084
181943
228168
276222
338580
394766
443922
458131
472156
501166
528770
564283
597730
6056 1 5
- -
--
Oct 17 1995 823PM P02 From LTTS OF Mfl INC PHONE No 617 438 S21S
GRftIN SIZE DISTRIBUTION TEST REPORT C c c e
100 i i ^ i i 7 ^ d bdquo bdquo j laquo ii i A j
bdquo9 bdquo
a 2 - a i
t sh
90 X
N^
B0 raquo m lts
-bull
70 Sk
gtia
Npound G0 shyu
550 gt
UJ bullshy
1u S pound 40 0 ^
30 bull i 20
10
0 2Q 0 1SG 100 10 01 aai 00UL
CRflIM CISC - mm
Test X +3 bull4 GRAVEL bull SflMD bull SILT bull DRY uses LL PI
t 16 00 2Z 3 521 256 SC-SM
SIEVE PERCENT FINCR STEVE PERCENT FINCR Uact on Incrwi nuwtoer ilz ilzi bull flUNSON ST PEABODC
bull bull a 96 3 4 777
15 95 10 714 1 92 e 20 607 Descr pt ion
075 90 40 505 bullSILTY CLAYEY GflNO 0 375 34 50 44 4
100 343
3X1 GRAIN SIZE 200 257
8804D60
gtDia Remarks
xC COEFh 1C1CNT5 UTS OF MASSACHUSETTS INC bull
SS1T to 1 u
Pro jlt-r t No UTS OF naSSACHLKKI lgt IMC Project) CftLCM flCHSCC
5 Richardson Lane
GtoneHam Mft 03 IBB Date 101195 Gamn 1 c- No 44fi1A
Figure 1
From UTS OF Mfl INC PHONE No 517 438 6216 Oct 17 1995 824PM F03
SOT ANALYSIS REPORT FOR NEW LAWN 101195
SOIL AND PLANT TISSUE TESTING LABWEST EXPERIMENT STATIONUNIVERSITY OF MASBACIIUfiFTTr AMHERST MA 01003
LAB NUMBER 3951010-107 BAG NUMBER 23467
DATE BFNT f
SOIL FROM COUNTY SOIL WEIGHT 537 g5cn CROP TURFORASS
UTS OF MASS INC COMMENTS ORGANIC MATTER 6 RICHARDSON LANE STONEHAM MA 02180
SAMPLE ID 4461B
LIMESTONE AND FERTILIZER RECOMMCNDATIONS FOR NEW LAWN CONSTRUCTION
No limestone ia required If peat mooc or similar material ia to be incorporated) see enclosed fact sheet
Fertilizer (per 10OO sq ft) 2 1ba N 2 Ibo P2O5 and O 1 bs KZO
Many fertilizer sources and rates may combine to provide acceptable turfgraes establ iahmont either from seed or aod One or two options baaed on this soil teat follow
Incorporate EITHER a 17-23-6 starter fert111zar at 10 lbs1000 sq ft OR a 30-3-3 lawn fertilizer at 7 1b81000 aq ft plus a 0-45-0 (triple superphosphate) fertilizer at 4 lbs1000 aq ft Hnto the top 3 to 4 inches of soil Retest Bull ona year after turf establishment
PLEASE read the enclosed fact sheets for niora specific Information on fertilization and liming procadurea
SOIL pH 71 NITROGEN NO3-N = Oa ppm NH4-N = 5 ppm BUFFER pH 74 ORGANIC MATTER 72 X (Desirable range 4-10X)
NUTRIENT_LEVELS_PPM_| Low Medium High Very High Phosphorus (P) 8 |XXXXXXXXXXXXX Potaaaium (K) 292 [XXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXX Calcium (Ca) 237S XXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXX Magnesium (Mg) 237 JXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXX
CATION EXCII CAP PERCENT BASE SATURATION MICRONUTRIENT LEVELS 130 Meq100g K= 52 Mg=134 Ca=816 ALL NORMAL
CXTRACTABLE ALUMINUM 41 ppm (Soil ranglaquo 10-250 ppm)
The lead level in thio soil 1s low
COMPUTER PROGRAM5-RECOMMENDATIONRbYOtHIOFPtANT~ampSOILSCI UMASS-AMHERST
Figure 2
TARGET SHEET
THE MATERIAL DESCRIBED BELOW WAS NOT SCANNED BECAUSE
(X) OVERSIZED
() NON-PAPER MEDIA
() OTHER
DESCRIPTION DOC 14732 DRAFT FINAL REMEDIAL CONSTRUCTION REPORT FIGURE 3 TOPOGRAPHIC PLAN SL-4 AREA BOTTOM OF FLY ASH SALEM ACRES SHEET 1 OF 1
THE OMITTED MATERIAL IS AVAILABLE FOR REVIEW BY APPOINTMENT
AT THE EPA NEW ENGLAND SUPERFUND RECORDS CENTER BOSTON MA
TARGET SHEET
THE MATERIAL DESCRIBED BELOW WAS NOT SCANNED BECAUSE
(X) OVERSIZED
() NON-PAPER MEDIA
() OTHER
DESCRIPTION DOC 14732 DRAFT FINAL REMEDIAL CONSTRUCTION REPORT FIGURE 4 TOPOGRAPHIC PLAN SL-4 AREA LIMIT OF REMEDIATION SALEM ACRES SHEET 1OF1
THE OMITTED MATERIAL IS AVAILABLE FOR REVIEW BY APPOINTMENT
AT THE EPA NEW ENGLAND SUPERFUND RECORDS CENTER BOSTON MA
TARGET SHEET
THE MATERIAL DESCRIBED BELOW WAS NOT SCANNED BECAUSE
(X) OVERSIZED
() NON-PAPER MEDIA
() OTHER
DESCRIPTION DOC 14732 DRAFT FINAL REMEDIAL CONSTRUCTION REPORT FIGURE 5 TOPOGRAPHIC PLAN SL-4 AREA AS-BUILT PLAN SALEM ACRES SHEET 1 OF 1
THE OMITTED MATERIAL IS AVAILABLE FOR REVIEW BY APPOINTMENT
AT THE EPA NEW ENGLAND SUPERFUND RECORDS CENTER BOSTON MA
(i)
^mft^m
VIEW OF BARCELONA AVENUE THROUGH ENTRANCE GATE PRECONT RUCTION
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(2)
VIEW OF ACCESS ROAD LOOKING NORTH SL-4 ON LEFT PRECONSTRUCTION
VIEW OF ACCESS ROAD LOOKING NORTH SL-4 ON LEFT DA-1 TO LEFT OF PICKUP TRUCK
PRECONSTRUCTION
(3)
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
O ID a CO z O OHI
CO UJ
OO_l
t CO ii-O
(5)
VIEW OF BOUNDARY BETWEEN SL-4 AND DA-1 LOOKING WEST PRECONSTRUCTION
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(6)
EROSION CONTROLS LOOKING NORTH FROM CORNER OF SL-4SL-5 ADJACENT TO WA-1 PRECONSTRUCTION
(7)
TRUCK LOADING PAD LOOKING NORTHWEST FROM SUPPORT ZONE
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(8)
DECONTAMINATION PAD LOOKING NORTHWEST FROM SUPPORT ZONE
(9)
EXCAVATION OF FLY ASH LOOKING NORTHWEST FROM CRZ NOTE WATER FOR DUST CONTROL
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(10)
VIEW LOOKING WEST AFTER REMOVAL OF FLY ASH NOTE WA-1 BEYOND EROSION CONTROLS
(11)
EXCAVATION OF CONTAMINATED OVERBURDEN LOOKING SOUTH FROM DA-1 BOUNDARY
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(12)
VIEW OF RESTORED SITE LOOKING WEST TOWARD WA-1
0
ltu
wsectbull
D Q
O
O z ^ O O_J LJJ
Q LJJ a o te LJJ
eg 3
(14)
VIEW OF RESTORED SITE LOOKING NORTH TOWARD DA-1 ALONG ACCESS ROAD
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(15)
gtbull bdquobdquo -
VIEW OF RESTORED SITE LOOKING SOUTH TOWARD SL-5
iu O
of bullo
01 u I ltO
w
o B ltabulls to 10
3
I Q Z
O m ^mdash
i sect^^ nu0 (- co^gtW IO - z zilaquo O O 5gl
oLU uj
V) LUo a o LU
(17)
VIEW OF RESTORED SITE ON DA-1 SJDE OF FENCE - LOOKING ST
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(18)
VIEW OF RESTORED SITE ON DA-1 SIDE OF FENCE - LOOKING WEST SL-4 ON RIGHT
APPENDIX A
ANALYTICAL RESULTS FOR
PONDED WATER
110795 1638 copy617 890 3883 TMA-WALTHAM ] 002007
PRELIMINARY REPORT UNAUDITED RESULTS
Thenno Analytical 300 Second Avenue PO Box 521 Waltham HA 02254
Attn Client Services Phone (617) 890-7200
Cashins amp Associates Order S5-11-034 55 Cambridge Street Date 110795 1522 Burlington HA 01803 Work ID Salem Acres Water
Date Received 110295 Attn Bob Cashins Date Completed
Purchase Order NA Invoice Number Client Code CASHINS
SAMPLE IDENTIFICATION
Sample Sample Number Description 01 11019S-924-01A
Sample Number 04
Sample Description
110195-9Z4-01D 02 110195-924-01B 05 110195-924-01E 03 110195-924-01C
Certified By
110795 1638 copy617 890 3883 TMA-WALTHAM 003007
PRELIMINARY REPORT UNAUDITED RESULTS
Order f S5-11-034 Thermo Analytical Page 2 110795 1522 TEST RESULTS BY SAHPLE
Test Description Volatile Organics- Aqueous Method EPA_8240 Test Code Collected 110195 02-00 Category WATER
DATE INJECTED 110695 DILUTION FACTOR 100 All results reported 1n ugL
COMPOUND RESULT DET LIMIT COMPOUND RESULT
Chloromethane U 10 Broroodi chl oromethane U Vinyl Chloride U 10 2-Chloroethyl Vinyl Ether U
Bromxnethane U 10 4-dethyl -2-pentanone U Chloroethane U 10 c1 3-1 3-Di chl oropropene U
Trichlorofluoronwthane U 50 Tol uene U Acetone 17 10 trans-1 3-Di chl oropropene LI
11-Oichloroethene U 50 11 2-Tri chl oroethane J Carbon Dlsulfide U 50 2-Hexanone U
Methyl ene Chloride U 50 Tetrachl oroethene U 12-Oichloroethene (total) U 50 D1 bromochl oromethane U
11-01 Chloroethane U 50 Chlorobenzene U Vinyl Acetate U 10 Ethyl benzene U
2-Butanone U 10 in and p-Xylene U Chloroform U 50 o-Xylene U
111-Tri Chloroethane U 50 Styrene U Carbon Tetrachlortde U 50 Broraoform U
Benzene U 50 112 2-Tat rachl oroethane U 12-01 Chloroethane U 50 1 3-01 chl orobenzene U
Trichloroethene U 50 I 4-Di chl orobenzene U 12-Dichloropropane U 50 12-01 chl orobenzene U
SURROGATE STANDARDS RESULT LEVEL X RECOVERY
12-Dichloroethane-D4 52 50 104 Toluene-08 47 50 94
l-Bromo-4-fluorobenzene 56 50 112
NOTES AND DEFINITIONS FOR THIS REPORT U =bull Undetected at stated detection limit
VOAJI
OET LIMIT
50 50
10 50 50 50 50 10
5 0 50 5 0 5 0 50 50 50 50 50 50 50 50
110795 1639 copy617 890 3883 TMA-WALTHAM copy004007
PRELIMINARY REPORT UNAUDITED RESULTS
Order t S5-11-034 Thermo Analytical Page 4 110795 1522 TEST RESULTS BY SAMPLE
ianple Description 110195-924-010 Lab No 04A Test Description RCRA Metals 1n Water Method SW846 Test Code
Collected 110195 0200 Category WATER
METAL RESULT DETECTION LIMIT METAL RESULT DETECTION LIMIT
Ag Silver U 10 As Arsenic 870 50
Ba Bar inn B69 10 Pb Lead U 50
Cd Cadmium U 50 Se Sel en1 um Z15 50
Cr Chromi um U 20 Hg Mercury U 020
NOTES AND DEFINITIONS FOR THIS REPORT All results reported in ugL U gt Undetected at stated detection limit
110795 1640 Q617 890 3883 TMA-WALTHAM 0005007
PRELIMINARY REPORT UNAUDITED RESULTS
Order S5-11-034 Thermo Analytical Page 5 110795 1522 REGULAR TEST RESULTS BY TEST
Chemical Oxygen Demand Mlnimun Maximum Method EPA600 4101
Sap Sample Description Result Units Limit Prepared Analyzed By 05A 110195-924-01E 64 bullgL 50 110395 110395 JD
Petroleum Hydrocarbons-H20 Minimum Maximum Method EPA600 4181
Samp Sample Description Result Units Limit Prepared Analyzed By 01A 110195-924-01A 108 mgL 050 110395 110395 JO
110795 1640 reg617 890 3883 TMA-WALTHAM copy006007
PRELIMINARY REPORT UNAUDITED RESULTS
Order I S5-11-034 Therm Analytical Page 6 110795 1522 TEST METHODOLOGIES
USEPA Test Methods for Evaluating Solid Wastes (SUS46 Third Edition) Method 7470 - Preparation of water for Mercury analysis
USEPA Test Methods for Evaluating Solid Vastes (SW846 Third Edition) Method 3010 - Add digestion of aqueous samples and extracts for total metals for analysis by Flame Atomic Absorption Spectroscopy or Inductively Coupled Plasma Spectroscopy
USEPA Test Methods for Evaluating Solid Vastes (SWB46 Third Edition Method 8270 mdash Gas ChroroatographyMass Spectrometry for PAHs
Volatile Organics in Water - Hazardous Substance List
SV846 Method 8240 - Modified
Test Methods for Evaluating Solid Waste SU-846 US EPA Office of Solid Waste and Emergency Response Washington 3rd Edition
Aqueous sanples are analyzed in accordance with Method 8240 using a purge and trap technique followed by 64s ChromatographyMass Spectroscopy
Quality assurance procedures for GCMS Include daily tuning and calibration of the mass spectrometer and the use of surrogate standards in each sample to monitor method performance Quantitatton is performed by the Internal standard method Analysis of blanks duplicate samples and standards are run frequently as further quality assurance procedures
USEPA Test Methods for Evaluating Solid Wastes (SW846 Third Edition) Method 3S10 mdash Separatory Funnel Liquid-Liquid Extraction
EPA-6004-79-020 - Chemical Oxygen Demand - Titrimetric Mid-Level Method 4101
EPA6004-79-020 - Petroleum Hydrocarbons 1n Water Total Recoverable Method 4181 (Spectrophotometric Infrared)
110795 1641 copy617 890 3883 TMA-WALTHAM copy007007
APPENDIX B
QUANTITY SURVEY DOCUMENTATION
TFMORAN INC Surveying - Engineering - Land Planning SoilsWetlands Mapping - Landscape Architecture
January 15 1996
Mr Jack Enos Vice President TFord Company Inc 118 Tenney Street Georgetown MA 01833
RE Survey Results - Salem Acres - SL4 Area Salem Massachusetts
Dear Jack
This letter amends the letter of December 13 1995 per our review last week
TFMoran Inc performed topographic surveys at the Salem Acres site on April 21 1994 for GEI Consultants prior to removal of material and for TFord Company on October 18 1995 after the removal of material The survey data from the original survey in 1994 was adjusted thirty feet higher to correct for a datum difference from current site datum This was due to the original reporting of the Site Benchmark (TP34) elevation as 11464 rather than 14464 which is the correct elevation
Once both topographic surfaces were on the site datum the raw cut volume was obtained by Eaglepoint (Volumes Module) Software utilizing the prismoidal method comparing the two surfaces For reference please see the attached topographic plan which superimposes the October 15 1995 contours (dark lines) over the April 21 1994 contours The volume is based on the intersection of the two surfaces Also it was noted that stock piles of material did exist on site which were not surveyed at the time
The final raw cut volume arrived at by the above methods is 12749 Cubic Yards
In November and December of 1995 the site was resurveyed to locate the area of exposed ledge at the site The results of this survey are shown on the attached topographic worksheet dated November 3 1995 and last revised January 15 1996 The results of the survey indicate the total site area to be 50860 sq ft or 117 acres The total area of exposed ledge surveyed is 19990 sq ft or 46 acres If you have any questions regarding the above call me directly Thank you
Sincerely
John W Myhaver Jr ^_ Field Operations Manager
Enclosure ItorLltr
Route 101 Bedford NH 03110 Phone (603) 472-4488 FAX (603) 472-9747
APPENDIX C
HEALTH AND SAFETY PHASE-OUT REPORT
HEALTH AND SAFETY PHASE-OUT REPORT SALEM ACRES SL-4 AREA
Introduction
During remediation work on SL-4 Health and Safety Monitoring was performed Cashins amp Associates Inc of Reading MA performed the following work as a subcontractor to TFCI
1) Preparation of a site-specific Health and Safety Plan (dated September 1 1995)
2) Provide a Field TechnicianIndustrial Hygienist to serve as Site Safety and Health Officer (SSHO) and to conduct air and noise monitoring
3) Provide a Certified Industrial Hygienist to review Health and Safety and to conduct site specific training (record of training included at end of Appendix C)
4) Collect 8-hour air samples for worker exposure and ambient air at the Barcelona Avenue gate Arrange for analysis of the samples and report results
5) Prepare daily and weekly Health and Safety reports
6) Prepare a Health and Safety Phase-Out Report
In general the following health and safety practices were followed
1) All workers wore hard hats safety glasses work boots gloves and hearing protection as minimum level PPE
2) When working in the exclusion zone workers wore in addition to above tyvek rubber overboots and rubber coated gloves When dust was a potential concern an industrial grade dustmist mask was also worn This level of PPE was considered Level D modified
3) Workers leaving the exclusion zone removed PPE (tyveks gloves boots and masks) in the support zone and either disposed of the items or decontaminated them
4) Workers andor visitors without 40-hour OSHA training were not permitted to enter the exclusion zone
Attached is a report prepared by Cashins amp Associates along with weekly Health and Safety Summary Reports prepared by the Field Hygienist In summary the air monitoring results indicate no levels exceeding the applicable exposure guidelines except one instance
During excavation of contaminated overburden in the northwest comer of the site an area of VOC contaminated soil was encountered Total VOCs levels measured using a PID exceeded the action level established in the Health and Safety Plan The SSHO advised TFCI to upgrade to Level C PPE in order to backfill the excavation in this area TFCI equipment operator upgraded and backfilled the area The SSHO in consultation with the Cashins CIH advised TFCI to avoid work in this area until the contaminants were characterized GEI sampled the material for waste characterization analysis and provided the results to TFCI Based on the results an action level was established by the CIH for the specific contaminants found Further PID measurements indicated levels below the new action level and work was resumed
The noise monitoring indicated that the noise level at the Barcelona Avenue gate was not exceeded Only one instance of excess noise level in the work zone was recorded (10 db(a) above the ambient noise level or 85 db(a)) Workers wore hearing protection in this instance
mdash 07171996 1601 6179444032 CASHIMS S ASSOCIATES PAGE 02
CASHINS amp Associates Inc
ItxhalrM Hy-gifnr A Invtronmtnltl Tttling
July 17 1996
Mr Jack Enos T Ford Company Inc USTenney Street Georgetown MA 01833
Dear Jack
The Site Safety and Health Officer (SSHO) from Cashing amp Associates Inc performed daily inspections of the SL-4 area Salem Acres Superfund Site between 9595 and 12195 in accordance with the Health amp Safety Plan (HSP) for the site Daily inspection logs were submitted every day No accidentsincidents were reported during the work period
In accordance with the Health amp Safety Plan the SSHO performed daily air and noise monitoring at the site during Ac project Samples were collected for metals (lead beryllium chromium arsenic) and Polynuclear Aromatic Hydrocarbons (PAHs) at the site perimeter and for workers exposure determination Coal Tar Pitch Volatiles (a benzene soluble extractables) were also used to determine the workers exposure to PAH compounds Coal Tar Pitch Volatiles (CTPV) were analyzed using OSHA 58 Method If CTPV levels oq personal samples exceed the site criteria of 02 ragm3 the sample was submitted for PAHs analysis All air samples on the site perimeter were analyzed for PAH compounds
Site monitoring air sample collection and results report were done under the supervision of a Certified Industrial Hygienist
Full shift personal worker exposure samples were collected once a week Ambient air samples were collected at the Barcelona Avenue gate about 20 feet to the west of the site gate to determine if site contaminants were migrating off site The ambient air samples were also collected once a week during the project except on rainy days and days without work with contaminated soil
All air samples were analyzed by the American Industrial Hygiene Association accredited ESA Laboratories Inc using the following methods PAHs - NIOSH 5515 Lead - NIOSH 7082 Beryllium - NIOSH 7102 Chromium - NIOSH 7024 Arsenic - NIOSH 7900 Coal Tar Pitch Volatiles - OSHA 58 All methods used are accepted by the industrial hygiene community for 8-hour exposure assessment EPA methods are usually used for ambient air measurements
CRErORTTFOmiOO
80 Mam Street bull Reading MA 01867 bull Phone- 61 7-944-4060 bull Fax 61 7-944-4082
07171996 1601 6179444032 CASHIMS amp ASSOCIATES PAGE 03
The results of air samples for metals and PAHs are presented in Table No 1
All concentrations of metals and PAHs at the site perimeter (Barcelona Avenue) and active work zones were below the OSHA Permissible Exposure Limits (PEL) and the American Conference of Governmental Industrial Hygicnists Threshold Limit Value (ACGIH TLV) Two personal samples collected on October 19 and October 23rd showed Coal Tar Pitch Volatiles (CTPV) results above OSHA PEL and AIHA TLV limits Both samples were resubmittcd to the lab for further analysis to determine if PAH compounds are present because the CTPV results were above site criteria
The results of the PAH concentrations for the personal sample on Mark Goodwin on October 19 1995 during excavation and washing trucks and for the personal sample on Ron Maker on October 23 1995 during excavating and cleaning rocks by compressed air were below OSHA PEL and ACGIH TLV limits
The SSHO performed noise monitoring according to the HSP at the exclusion zone and at the Barcelona Avenue site perimeter fence A Dupont sound level meter was used for noise monitoring The noise level in the exclusion zone during all operations except one did not exceed the on site criteria of 85 dB(a) During a short time when the air compressor had been used to clean rocks the sound level in the exclusion zone next to the air compressor did exceed 85 dB(a) Ear protection devices were worn by the workers during that operation At no time did the noise level at the Barcelona Avenue site perimeter exceed 10 dB(a) above the ambient noise level or 85 dB(a)
The SSHO performed total dust monitoring on a daily basis during the project at the site perimeter downwind of work location and at the site gate using a Miniram real time dust meter The summary of dust monitoring is presented in Table No 2 Total dust concentrations on site and off site did not exceed site criteria of 1 mgm3 and the action level of 05 nigny1
The summary of air monitoring for Volatile Organic Compounds (VOC) is presented in Table No 3 VOC concentrations in the working area did not exceed the on site criteria of 5 ppm in a breathing zone VOC concentrations on the site perimeter did not exceed real time off site criteria of 2 ppm
Five detail reports with results of air sampling were submitted during the project period
Sincerely Cashins amp Associates Inc
Evelina Vaughan Industrial Hygieflfst
CASHINS amp ASSOCIATES Inc
80 Mam Street bull Reading MA 01867 bull Phone61 7-944-4060 bull Fax 617-944-4082
07171996 1601 6179444082 CASHINS S ASSOCIATES PAGE 04
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DATE
LOCATION OF TRAINING $ALt_M ACu
TIME 9 ^ rW
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DATE poundLOCATION OF TRAINING
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CASHINS amp Associates Inc
Industrie Hygitmt amp tnvironmvnlal
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LOCATION OF TRAINING
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CASHINS amp Associates inc
Ifxtuitral Hygltne A fnvironmtnltt Tuning
W3SXLY HBALTH amp SAFETY PLAN COMPLIANCE SUMMARY R3PORT
CLIENT T foyd C o m a n
LOCATION gal era Acres Sx^perfund Site 8L-4 Area
DATES INCLUDED IN SUMMARY
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SUMMARIZED BY FOR CASHINS amp ASSOCIATES INC
55 CAMBRIDGE STREET bull SUITE 201 bull BURLINGTON MA 01803 laquo TEL 61 -273-9080 bull FAX 67-273-9C84
09111995 1023 6172739084 CASHINS ASSOCIATES PAGE 01
CASHINSamp Associates Inc
Induttrml Hygttnr t Emtroomtnttl Ttstinf
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Fprd Company
LOCATION Salen Acres Suoerfund Site SL-4 Area
DATES INCLUDED IN SUMMARY
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55 CAMBRIDGE STREET bull SUITE 201 bull BURLINGTON MA 01803 raquo- TEL 6J 7-273-9080 bull FAX 617-273-9084
CASHINS amp Associates Inc
Industrial Hygitnf amp CmimnmenUl Tinting
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Compan
LOCATION Salem Acres Superfund Site SL-4 Area
DATES INCLUDED IN SUMMARY
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07161996 1650 6179444082 CASHI MS amp ASSOCIATES PAGE 10
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CASHINSamp Associates Inc
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WEEKLY HEALTH 6 SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Fortjl Cqjapany
LOCATION Salem Acrlaquoa Superfund Site 9L-4 Area
DATES INCLUDED IN SUMMARY
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CLIENT T Ford Company
LOCATION Salem Acres Superfund Site SL-4 Area
DATES INCLUDED IN SUMMARY J_
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ISSUED BY REPRESENTING CASHINS S ASSOCIATES INcT DAY DATE ISSUED O04Xmdash 1 bull-bullmdashbull f P^JT
PROJECT NAME_ SITE LOCATION
THE PURPOSE OF THE FOLLOWING STATEMENT IS TO DOCUMENT THE EXISTENCE OF A CONDITION OR CONCERN WHICH CASHINS amp ASSOCIATES INC BELIEVES WARRANTS IMMEDIATE CORRECTIVE ACTION POSSIBLE SOLUTIONS AND OR CORRECTIVE ACTIONS WILL BE INCLUDED IN THIS NOTIFICATION WHEN POSSIBLE THIS NOTIFICATION IS LIMITED TO SITUATIONS THAT REPRESENT EITHER IMMEDIATE DANGER TO LIFE OR HEALTH CONDITIONS OR PREVIOUSLY IDENTIFIED CHRONIC PROBLEMS THAT UNDERMINE OUR ABILITY TO EFFECTIVELY INSURE COMPLIANCE WITH THE REQUIREMENTS OF THE HEALTH AND SAFETY PLAN
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CISHINS amp Associates Inc
Industrial Hygirne amp Cmimnmtntal Testing
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
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DATES INCLUDED IN SUMMARY T
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WEEKLY HEALTH amp SA7STT PLAN COMPLIANCE SUMMARY REPORT
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DATES INCLUDED IN SUMMARY bull
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07161996 1650 617944408 CASHING 3 ASSOCIATES PAGE 05
CASHINSamp Associates Inc
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DATES INCLUDED IN SUMMARYj pound mdashiffofrshy f
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55 CAMBRIDGE STREET bull SUITE 201 bull BURLINGTON MA 01803 lt TEL 617-273-9080 bull FAX 617-273-9084
CASHIMS amp ASSOCIATES PAGE 04 07161996 1658 6179444032
OVSHINSamp Associates Inc
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Company T
LOCATION Salem AcrM Suoerfund Stta 8L-4 Araa
DATES INCLUDED IN SUMMARY
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SUMMARIZED BY pound FOR CASHINS amp ASSOCIATES INC
55 CAMBRIDGE STREET bull SUITE 201 bull BURUNGTON MA 01803 bull TEL 617-273-9080 bull FAX 617-273-9084
07161996 1658 6179444082 CASHIMS 3 ASSOCIATES PAGE 03
CASHINSamp Associates Inc
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WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT ^
CLIENT T Ford Company t lP ~ ff2-r
LOCATION Sal era Acraa Suplaquorfund Sj-ta 8L-4 Araa
DATES INCLUDED IN SUMMARY
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55 CAMBRIDGE STREET bull SUITE 201 bull 8URUNGTON MA 01803 bull TEL 617-273-9080 bull FAX 617-273-90W
07151996 18 fO 6179444082 CASHINS S ASSOCIATES PAGE 02
CASHINS amp Associates Inc
WBBKLY HEALTH amp SAFETY FLAK COMPLIANCE SUMMARY REPORT
CLIENT T Ford Compapv
LOCATION i Sal am Acrlaquolaquo Suparfund Sita SL-4 Area
DATES INCLUDED IN SUMMARY i bull pound7 mdash
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SXWMARIZ2D BY FOR CASHINS amp ASSOCIATES INC (
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- barcode 14732
- barcodetext SEMS Doc ID 14732
![Page 13: SALEM ACRES SUPERFUND SITE SALEM, MA ...The truck loading pa d consisted of a crushed stone are sea t up along the east sid e o f SL-4 adjacent to the access road A. row of concrete](https://reader036.vdocuments.us/reader036/viewer/2022070114/60729b840fec4e6b4d136a16/html5/thumbnails/13.jpg)
TABLE 2 SUMMARY OF CONTAMINATED
OVERBURDEN REMOVAL SALEM ACRES SUPERFUND SITE SL-4 AREA
DATE
on 19 OCT 20
OCT 23
OCT 24
OCT 25
OCT 26
OCT 27
OCT 31
NOV 1
NOV2
NOV 6
NOV 8
NOV 9
NOV 21
NOV 28
DEC 7
NUMBER OF LOADS
14
14
14
13
14
16
18
18
12
4
4
8
8
8
9
2
DAILY TOTAL (TONS)
46121
41649
49314
448 59
46225
48054
62358
56186
491 56
14209
14025
29010
27604
35513
33447
7885
CUMULATIVE TOTAL (TONS)
46121
87770
137084
181943
228168
276222
338580
394766
443922
458131
472156
501166
528770
564283
597730
6056 1 5
- -
--
Oct 17 1995 823PM P02 From LTTS OF Mfl INC PHONE No 617 438 S21S
GRftIN SIZE DISTRIBUTION TEST REPORT C c c e
100 i i ^ i i 7 ^ d bdquo bdquo j laquo ii i A j
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550 gt
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1u S pound 40 0 ^
30 bull i 20
10
0 2Q 0 1SG 100 10 01 aai 00UL
CRflIM CISC - mm
Test X +3 bull4 GRAVEL bull SflMD bull SILT bull DRY uses LL PI
t 16 00 2Z 3 521 256 SC-SM
SIEVE PERCENT FINCR STEVE PERCENT FINCR Uact on Incrwi nuwtoer ilz ilzi bull flUNSON ST PEABODC
bull bull a 96 3 4 777
15 95 10 714 1 92 e 20 607 Descr pt ion
075 90 40 505 bullSILTY CLAYEY GflNO 0 375 34 50 44 4
100 343
3X1 GRAIN SIZE 200 257
8804D60
gtDia Remarks
xC COEFh 1C1CNT5 UTS OF MASSACHUSETTS INC bull
SS1T to 1 u
Pro jlt-r t No UTS OF naSSACHLKKI lgt IMC Project) CftLCM flCHSCC
5 Richardson Lane
GtoneHam Mft 03 IBB Date 101195 Gamn 1 c- No 44fi1A
Figure 1
From UTS OF Mfl INC PHONE No 517 438 6216 Oct 17 1995 824PM F03
SOT ANALYSIS REPORT FOR NEW LAWN 101195
SOIL AND PLANT TISSUE TESTING LABWEST EXPERIMENT STATIONUNIVERSITY OF MASBACIIUfiFTTr AMHERST MA 01003
LAB NUMBER 3951010-107 BAG NUMBER 23467
DATE BFNT f
SOIL FROM COUNTY SOIL WEIGHT 537 g5cn CROP TURFORASS
UTS OF MASS INC COMMENTS ORGANIC MATTER 6 RICHARDSON LANE STONEHAM MA 02180
SAMPLE ID 4461B
LIMESTONE AND FERTILIZER RECOMMCNDATIONS FOR NEW LAWN CONSTRUCTION
No limestone ia required If peat mooc or similar material ia to be incorporated) see enclosed fact sheet
Fertilizer (per 10OO sq ft) 2 1ba N 2 Ibo P2O5 and O 1 bs KZO
Many fertilizer sources and rates may combine to provide acceptable turfgraes establ iahmont either from seed or aod One or two options baaed on this soil teat follow
Incorporate EITHER a 17-23-6 starter fert111zar at 10 lbs1000 sq ft OR a 30-3-3 lawn fertilizer at 7 1b81000 aq ft plus a 0-45-0 (triple superphosphate) fertilizer at 4 lbs1000 aq ft Hnto the top 3 to 4 inches of soil Retest Bull ona year after turf establishment
PLEASE read the enclosed fact sheets for niora specific Information on fertilization and liming procadurea
SOIL pH 71 NITROGEN NO3-N = Oa ppm NH4-N = 5 ppm BUFFER pH 74 ORGANIC MATTER 72 X (Desirable range 4-10X)
NUTRIENT_LEVELS_PPM_| Low Medium High Very High Phosphorus (P) 8 |XXXXXXXXXXXXX Potaaaium (K) 292 [XXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXX Calcium (Ca) 237S XXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXX Magnesium (Mg) 237 JXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXX
CATION EXCII CAP PERCENT BASE SATURATION MICRONUTRIENT LEVELS 130 Meq100g K= 52 Mg=134 Ca=816 ALL NORMAL
CXTRACTABLE ALUMINUM 41 ppm (Soil ranglaquo 10-250 ppm)
The lead level in thio soil 1s low
COMPUTER PROGRAM5-RECOMMENDATIONRbYOtHIOFPtANT~ampSOILSCI UMASS-AMHERST
Figure 2
TARGET SHEET
THE MATERIAL DESCRIBED BELOW WAS NOT SCANNED BECAUSE
(X) OVERSIZED
() NON-PAPER MEDIA
() OTHER
DESCRIPTION DOC 14732 DRAFT FINAL REMEDIAL CONSTRUCTION REPORT FIGURE 3 TOPOGRAPHIC PLAN SL-4 AREA BOTTOM OF FLY ASH SALEM ACRES SHEET 1 OF 1
THE OMITTED MATERIAL IS AVAILABLE FOR REVIEW BY APPOINTMENT
AT THE EPA NEW ENGLAND SUPERFUND RECORDS CENTER BOSTON MA
TARGET SHEET
THE MATERIAL DESCRIBED BELOW WAS NOT SCANNED BECAUSE
(X) OVERSIZED
() NON-PAPER MEDIA
() OTHER
DESCRIPTION DOC 14732 DRAFT FINAL REMEDIAL CONSTRUCTION REPORT FIGURE 4 TOPOGRAPHIC PLAN SL-4 AREA LIMIT OF REMEDIATION SALEM ACRES SHEET 1OF1
THE OMITTED MATERIAL IS AVAILABLE FOR REVIEW BY APPOINTMENT
AT THE EPA NEW ENGLAND SUPERFUND RECORDS CENTER BOSTON MA
TARGET SHEET
THE MATERIAL DESCRIBED BELOW WAS NOT SCANNED BECAUSE
(X) OVERSIZED
() NON-PAPER MEDIA
() OTHER
DESCRIPTION DOC 14732 DRAFT FINAL REMEDIAL CONSTRUCTION REPORT FIGURE 5 TOPOGRAPHIC PLAN SL-4 AREA AS-BUILT PLAN SALEM ACRES SHEET 1 OF 1
THE OMITTED MATERIAL IS AVAILABLE FOR REVIEW BY APPOINTMENT
AT THE EPA NEW ENGLAND SUPERFUND RECORDS CENTER BOSTON MA
(i)
^mft^m
VIEW OF BARCELONA AVENUE THROUGH ENTRANCE GATE PRECONT RUCTION
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(2)
VIEW OF ACCESS ROAD LOOKING NORTH SL-4 ON LEFT PRECONSTRUCTION
VIEW OF ACCESS ROAD LOOKING NORTH SL-4 ON LEFT DA-1 TO LEFT OF PICKUP TRUCK
PRECONSTRUCTION
(3)
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
O ID a CO z O OHI
CO UJ
OO_l
t CO ii-O
(5)
VIEW OF BOUNDARY BETWEEN SL-4 AND DA-1 LOOKING WEST PRECONSTRUCTION
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(6)
EROSION CONTROLS LOOKING NORTH FROM CORNER OF SL-4SL-5 ADJACENT TO WA-1 PRECONSTRUCTION
(7)
TRUCK LOADING PAD LOOKING NORTHWEST FROM SUPPORT ZONE
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(8)
DECONTAMINATION PAD LOOKING NORTHWEST FROM SUPPORT ZONE
(9)
EXCAVATION OF FLY ASH LOOKING NORTHWEST FROM CRZ NOTE WATER FOR DUST CONTROL
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(10)
VIEW LOOKING WEST AFTER REMOVAL OF FLY ASH NOTE WA-1 BEYOND EROSION CONTROLS
(11)
EXCAVATION OF CONTAMINATED OVERBURDEN LOOKING SOUTH FROM DA-1 BOUNDARY
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(12)
VIEW OF RESTORED SITE LOOKING WEST TOWARD WA-1
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VIEW OF RESTORED SITE ON DA-1 SIDE OF FENCE - LOOKING WEST SL-4 ON RIGHT
APPENDIX A
ANALYTICAL RESULTS FOR
PONDED WATER
110795 1638 copy617 890 3883 TMA-WALTHAM ] 002007
PRELIMINARY REPORT UNAUDITED RESULTS
Thenno Analytical 300 Second Avenue PO Box 521 Waltham HA 02254
Attn Client Services Phone (617) 890-7200
Cashins amp Associates Order S5-11-034 55 Cambridge Street Date 110795 1522 Burlington HA 01803 Work ID Salem Acres Water
Date Received 110295 Attn Bob Cashins Date Completed
Purchase Order NA Invoice Number Client Code CASHINS
SAMPLE IDENTIFICATION
Sample Sample Number Description 01 11019S-924-01A
Sample Number 04
Sample Description
110195-9Z4-01D 02 110195-924-01B 05 110195-924-01E 03 110195-924-01C
Certified By
110795 1638 copy617 890 3883 TMA-WALTHAM 003007
PRELIMINARY REPORT UNAUDITED RESULTS
Order f S5-11-034 Thermo Analytical Page 2 110795 1522 TEST RESULTS BY SAHPLE
Test Description Volatile Organics- Aqueous Method EPA_8240 Test Code Collected 110195 02-00 Category WATER
DATE INJECTED 110695 DILUTION FACTOR 100 All results reported 1n ugL
COMPOUND RESULT DET LIMIT COMPOUND RESULT
Chloromethane U 10 Broroodi chl oromethane U Vinyl Chloride U 10 2-Chloroethyl Vinyl Ether U
Bromxnethane U 10 4-dethyl -2-pentanone U Chloroethane U 10 c1 3-1 3-Di chl oropropene U
Trichlorofluoronwthane U 50 Tol uene U Acetone 17 10 trans-1 3-Di chl oropropene LI
11-Oichloroethene U 50 11 2-Tri chl oroethane J Carbon Dlsulfide U 50 2-Hexanone U
Methyl ene Chloride U 50 Tetrachl oroethene U 12-Oichloroethene (total) U 50 D1 bromochl oromethane U
11-01 Chloroethane U 50 Chlorobenzene U Vinyl Acetate U 10 Ethyl benzene U
2-Butanone U 10 in and p-Xylene U Chloroform U 50 o-Xylene U
111-Tri Chloroethane U 50 Styrene U Carbon Tetrachlortde U 50 Broraoform U
Benzene U 50 112 2-Tat rachl oroethane U 12-01 Chloroethane U 50 1 3-01 chl orobenzene U
Trichloroethene U 50 I 4-Di chl orobenzene U 12-Dichloropropane U 50 12-01 chl orobenzene U
SURROGATE STANDARDS RESULT LEVEL X RECOVERY
12-Dichloroethane-D4 52 50 104 Toluene-08 47 50 94
l-Bromo-4-fluorobenzene 56 50 112
NOTES AND DEFINITIONS FOR THIS REPORT U =bull Undetected at stated detection limit
VOAJI
OET LIMIT
50 50
10 50 50 50 50 10
5 0 50 5 0 5 0 50 50 50 50 50 50 50 50
110795 1639 copy617 890 3883 TMA-WALTHAM copy004007
PRELIMINARY REPORT UNAUDITED RESULTS
Order t S5-11-034 Thermo Analytical Page 4 110795 1522 TEST RESULTS BY SAMPLE
ianple Description 110195-924-010 Lab No 04A Test Description RCRA Metals 1n Water Method SW846 Test Code
Collected 110195 0200 Category WATER
METAL RESULT DETECTION LIMIT METAL RESULT DETECTION LIMIT
Ag Silver U 10 As Arsenic 870 50
Ba Bar inn B69 10 Pb Lead U 50
Cd Cadmium U 50 Se Sel en1 um Z15 50
Cr Chromi um U 20 Hg Mercury U 020
NOTES AND DEFINITIONS FOR THIS REPORT All results reported in ugL U gt Undetected at stated detection limit
110795 1640 Q617 890 3883 TMA-WALTHAM 0005007
PRELIMINARY REPORT UNAUDITED RESULTS
Order S5-11-034 Thermo Analytical Page 5 110795 1522 REGULAR TEST RESULTS BY TEST
Chemical Oxygen Demand Mlnimun Maximum Method EPA600 4101
Sap Sample Description Result Units Limit Prepared Analyzed By 05A 110195-924-01E 64 bullgL 50 110395 110395 JD
Petroleum Hydrocarbons-H20 Minimum Maximum Method EPA600 4181
Samp Sample Description Result Units Limit Prepared Analyzed By 01A 110195-924-01A 108 mgL 050 110395 110395 JO
110795 1640 reg617 890 3883 TMA-WALTHAM copy006007
PRELIMINARY REPORT UNAUDITED RESULTS
Order I S5-11-034 Therm Analytical Page 6 110795 1522 TEST METHODOLOGIES
USEPA Test Methods for Evaluating Solid Wastes (SUS46 Third Edition) Method 7470 - Preparation of water for Mercury analysis
USEPA Test Methods for Evaluating Solid Vastes (SW846 Third Edition) Method 3010 - Add digestion of aqueous samples and extracts for total metals for analysis by Flame Atomic Absorption Spectroscopy or Inductively Coupled Plasma Spectroscopy
USEPA Test Methods for Evaluating Solid Vastes (SWB46 Third Edition Method 8270 mdash Gas ChroroatographyMass Spectrometry for PAHs
Volatile Organics in Water - Hazardous Substance List
SV846 Method 8240 - Modified
Test Methods for Evaluating Solid Waste SU-846 US EPA Office of Solid Waste and Emergency Response Washington 3rd Edition
Aqueous sanples are analyzed in accordance with Method 8240 using a purge and trap technique followed by 64s ChromatographyMass Spectroscopy
Quality assurance procedures for GCMS Include daily tuning and calibration of the mass spectrometer and the use of surrogate standards in each sample to monitor method performance Quantitatton is performed by the Internal standard method Analysis of blanks duplicate samples and standards are run frequently as further quality assurance procedures
USEPA Test Methods for Evaluating Solid Wastes (SW846 Third Edition) Method 3S10 mdash Separatory Funnel Liquid-Liquid Extraction
EPA-6004-79-020 - Chemical Oxygen Demand - Titrimetric Mid-Level Method 4101
EPA6004-79-020 - Petroleum Hydrocarbons 1n Water Total Recoverable Method 4181 (Spectrophotometric Infrared)
110795 1641 copy617 890 3883 TMA-WALTHAM copy007007
APPENDIX B
QUANTITY SURVEY DOCUMENTATION
TFMORAN INC Surveying - Engineering - Land Planning SoilsWetlands Mapping - Landscape Architecture
January 15 1996
Mr Jack Enos Vice President TFord Company Inc 118 Tenney Street Georgetown MA 01833
RE Survey Results - Salem Acres - SL4 Area Salem Massachusetts
Dear Jack
This letter amends the letter of December 13 1995 per our review last week
TFMoran Inc performed topographic surveys at the Salem Acres site on April 21 1994 for GEI Consultants prior to removal of material and for TFord Company on October 18 1995 after the removal of material The survey data from the original survey in 1994 was adjusted thirty feet higher to correct for a datum difference from current site datum This was due to the original reporting of the Site Benchmark (TP34) elevation as 11464 rather than 14464 which is the correct elevation
Once both topographic surfaces were on the site datum the raw cut volume was obtained by Eaglepoint (Volumes Module) Software utilizing the prismoidal method comparing the two surfaces For reference please see the attached topographic plan which superimposes the October 15 1995 contours (dark lines) over the April 21 1994 contours The volume is based on the intersection of the two surfaces Also it was noted that stock piles of material did exist on site which were not surveyed at the time
The final raw cut volume arrived at by the above methods is 12749 Cubic Yards
In November and December of 1995 the site was resurveyed to locate the area of exposed ledge at the site The results of this survey are shown on the attached topographic worksheet dated November 3 1995 and last revised January 15 1996 The results of the survey indicate the total site area to be 50860 sq ft or 117 acres The total area of exposed ledge surveyed is 19990 sq ft or 46 acres If you have any questions regarding the above call me directly Thank you
Sincerely
John W Myhaver Jr ^_ Field Operations Manager
Enclosure ItorLltr
Route 101 Bedford NH 03110 Phone (603) 472-4488 FAX (603) 472-9747
APPENDIX C
HEALTH AND SAFETY PHASE-OUT REPORT
HEALTH AND SAFETY PHASE-OUT REPORT SALEM ACRES SL-4 AREA
Introduction
During remediation work on SL-4 Health and Safety Monitoring was performed Cashins amp Associates Inc of Reading MA performed the following work as a subcontractor to TFCI
1) Preparation of a site-specific Health and Safety Plan (dated September 1 1995)
2) Provide a Field TechnicianIndustrial Hygienist to serve as Site Safety and Health Officer (SSHO) and to conduct air and noise monitoring
3) Provide a Certified Industrial Hygienist to review Health and Safety and to conduct site specific training (record of training included at end of Appendix C)
4) Collect 8-hour air samples for worker exposure and ambient air at the Barcelona Avenue gate Arrange for analysis of the samples and report results
5) Prepare daily and weekly Health and Safety reports
6) Prepare a Health and Safety Phase-Out Report
In general the following health and safety practices were followed
1) All workers wore hard hats safety glasses work boots gloves and hearing protection as minimum level PPE
2) When working in the exclusion zone workers wore in addition to above tyvek rubber overboots and rubber coated gloves When dust was a potential concern an industrial grade dustmist mask was also worn This level of PPE was considered Level D modified
3) Workers leaving the exclusion zone removed PPE (tyveks gloves boots and masks) in the support zone and either disposed of the items or decontaminated them
4) Workers andor visitors without 40-hour OSHA training were not permitted to enter the exclusion zone
Attached is a report prepared by Cashins amp Associates along with weekly Health and Safety Summary Reports prepared by the Field Hygienist In summary the air monitoring results indicate no levels exceeding the applicable exposure guidelines except one instance
During excavation of contaminated overburden in the northwest comer of the site an area of VOC contaminated soil was encountered Total VOCs levels measured using a PID exceeded the action level established in the Health and Safety Plan The SSHO advised TFCI to upgrade to Level C PPE in order to backfill the excavation in this area TFCI equipment operator upgraded and backfilled the area The SSHO in consultation with the Cashins CIH advised TFCI to avoid work in this area until the contaminants were characterized GEI sampled the material for waste characterization analysis and provided the results to TFCI Based on the results an action level was established by the CIH for the specific contaminants found Further PID measurements indicated levels below the new action level and work was resumed
The noise monitoring indicated that the noise level at the Barcelona Avenue gate was not exceeded Only one instance of excess noise level in the work zone was recorded (10 db(a) above the ambient noise level or 85 db(a)) Workers wore hearing protection in this instance
mdash 07171996 1601 6179444032 CASHIMS S ASSOCIATES PAGE 02
CASHINS amp Associates Inc
ItxhalrM Hy-gifnr A Invtronmtnltl Tttling
July 17 1996
Mr Jack Enos T Ford Company Inc USTenney Street Georgetown MA 01833
Dear Jack
The Site Safety and Health Officer (SSHO) from Cashing amp Associates Inc performed daily inspections of the SL-4 area Salem Acres Superfund Site between 9595 and 12195 in accordance with the Health amp Safety Plan (HSP) for the site Daily inspection logs were submitted every day No accidentsincidents were reported during the work period
In accordance with the Health amp Safety Plan the SSHO performed daily air and noise monitoring at the site during Ac project Samples were collected for metals (lead beryllium chromium arsenic) and Polynuclear Aromatic Hydrocarbons (PAHs) at the site perimeter and for workers exposure determination Coal Tar Pitch Volatiles (a benzene soluble extractables) were also used to determine the workers exposure to PAH compounds Coal Tar Pitch Volatiles (CTPV) were analyzed using OSHA 58 Method If CTPV levels oq personal samples exceed the site criteria of 02 ragm3 the sample was submitted for PAHs analysis All air samples on the site perimeter were analyzed for PAH compounds
Site monitoring air sample collection and results report were done under the supervision of a Certified Industrial Hygienist
Full shift personal worker exposure samples were collected once a week Ambient air samples were collected at the Barcelona Avenue gate about 20 feet to the west of the site gate to determine if site contaminants were migrating off site The ambient air samples were also collected once a week during the project except on rainy days and days without work with contaminated soil
All air samples were analyzed by the American Industrial Hygiene Association accredited ESA Laboratories Inc using the following methods PAHs - NIOSH 5515 Lead - NIOSH 7082 Beryllium - NIOSH 7102 Chromium - NIOSH 7024 Arsenic - NIOSH 7900 Coal Tar Pitch Volatiles - OSHA 58 All methods used are accepted by the industrial hygiene community for 8-hour exposure assessment EPA methods are usually used for ambient air measurements
CRErORTTFOmiOO
80 Mam Street bull Reading MA 01867 bull Phone- 61 7-944-4060 bull Fax 61 7-944-4082
07171996 1601 6179444032 CASHIMS amp ASSOCIATES PAGE 03
The results of air samples for metals and PAHs are presented in Table No 1
All concentrations of metals and PAHs at the site perimeter (Barcelona Avenue) and active work zones were below the OSHA Permissible Exposure Limits (PEL) and the American Conference of Governmental Industrial Hygicnists Threshold Limit Value (ACGIH TLV) Two personal samples collected on October 19 and October 23rd showed Coal Tar Pitch Volatiles (CTPV) results above OSHA PEL and AIHA TLV limits Both samples were resubmittcd to the lab for further analysis to determine if PAH compounds are present because the CTPV results were above site criteria
The results of the PAH concentrations for the personal sample on Mark Goodwin on October 19 1995 during excavation and washing trucks and for the personal sample on Ron Maker on October 23 1995 during excavating and cleaning rocks by compressed air were below OSHA PEL and ACGIH TLV limits
The SSHO performed noise monitoring according to the HSP at the exclusion zone and at the Barcelona Avenue site perimeter fence A Dupont sound level meter was used for noise monitoring The noise level in the exclusion zone during all operations except one did not exceed the on site criteria of 85 dB(a) During a short time when the air compressor had been used to clean rocks the sound level in the exclusion zone next to the air compressor did exceed 85 dB(a) Ear protection devices were worn by the workers during that operation At no time did the noise level at the Barcelona Avenue site perimeter exceed 10 dB(a) above the ambient noise level or 85 dB(a)
The SSHO performed total dust monitoring on a daily basis during the project at the site perimeter downwind of work location and at the site gate using a Miniram real time dust meter The summary of dust monitoring is presented in Table No 2 Total dust concentrations on site and off site did not exceed site criteria of 1 mgm3 and the action level of 05 nigny1
The summary of air monitoring for Volatile Organic Compounds (VOC) is presented in Table No 3 VOC concentrations in the working area did not exceed the on site criteria of 5 ppm in a breathing zone VOC concentrations on the site perimeter did not exceed real time off site criteria of 2 ppm
Five detail reports with results of air sampling were submitted during the project period
Sincerely Cashins amp Associates Inc
Evelina Vaughan Industrial Hygieflfst
CASHINS amp ASSOCIATES Inc
80 Mam Street bull Reading MA 01867 bull Phone61 7-944-4060 bull Fax 617-944-4082
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89111995 1023 6172733(384 CASHINS ASSOCIATES PAGE 01
CASHINS amp Associates inc
Ifxtuitral Hygltne A fnvironmtnltt Tuning
W3SXLY HBALTH amp SAFETY PLAN COMPLIANCE SUMMARY R3PORT
CLIENT T foyd C o m a n
LOCATION gal era Acres Sx^perfund Site 8L-4 Area
DATES INCLUDED IN SUMMARY
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SUMMARIZED BY FOR CASHINS amp ASSOCIATES INC
55 CAMBRIDGE STREET bull SUITE 201 bull BURLINGTON MA 01803 laquo TEL 61 -273-9080 bull FAX 67-273-9C84
09111995 1023 6172739084 CASHINS ASSOCIATES PAGE 01
CASHINSamp Associates Inc
Induttrml Hygttnr t Emtroomtnttl Ttstinf
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
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LOCATION Salen Acres Suoerfund Site SL-4 Area
DATES INCLUDED IN SUMMARY
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55 CAMBRIDGE STREET bull SUITE 201 bull BURLINGTON MA 01803 raquo- TEL 6J 7-273-9080 bull FAX 617-273-9084
CASHINS amp Associates Inc
Industrial Hygitnf amp CmimnmenUl Tinting
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Compan
LOCATION Salem Acres Superfund Site SL-4 Area
DATES INCLUDED IN SUMMARY
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WEEKLY HEALTH amp SAFBTT PLAN COMPLIANCE SUMMARY REPORT
CLIENT ^T Ford Combanv
LOCATION Salam Aerag SL-4
DATES INCLUDED IN SUMMARY
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07161996 1650 6179444082 CASH INS amp ASSOCIATES PAGE 08
CASHINSamp Associates Inc
Intutttitl Myffcnt t InvtmnmmUt Itnl
WEEKLY HEALTH 6 SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Fortjl Cqjapany
LOCATION Salem Acrlaquoa Superfund Site 9L-4 Area
DATES INCLUDED IN SUMMARY
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SUMMARIZED BY FOR CASKINS amp ASSOCIATES INC
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77
OSHINSamp Associates Inc
Industrial Hygiene amp Emironmvntal Testing
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Company
LOCATION Salem Acres Superfund Site SL-4 Area
DATES INCLUDED IN SUMMARY J_
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SUMMARIZED BY FOR CASHINS amp ASSOCIATES INC
5 CAMBRIDGE STREET bull SUITE JO I bull BURLINGTON MA 01 K03 TEL ltjl 7-J7J-9080 bull FAX b I 7-273-9084
CASHINS amp Associates Inc
Industrial Hygifnr amp [nvironmenljl res
SERIOUS HAZARD NOTIFICATION
ISSUED TO REPRESENTING
ISSUED BY REPRESENTING CASHINS S ASSOCIATES INcT DAY DATE ISSUED O04Xmdash 1 bull-bullmdashbull f P^JT
PROJECT NAME_ SITE LOCATION
THE PURPOSE OF THE FOLLOWING STATEMENT IS TO DOCUMENT THE EXISTENCE OF A CONDITION OR CONCERN WHICH CASHINS amp ASSOCIATES INC BELIEVES WARRANTS IMMEDIATE CORRECTIVE ACTION POSSIBLE SOLUTIONS AND OR CORRECTIVE ACTIONS WILL BE INCLUDED IN THIS NOTIFICATION WHEN POSSIBLE THIS NOTIFICATION IS LIMITED TO SITUATIONS THAT REPRESENT EITHER IMMEDIATE DANGER TO LIFE OR HEALTH CONDITIONS OR PREVIOUSLY IDENTIFIED CHRONIC PROBLEMS THAT UNDERMINE OUR ABILITY TO EFFECTIVELY INSURE COMPLIANCE WITH THE REQUIREMENTS OF THE HEALTH AND SAFETY PLAN
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ACKNOWLEDGEMENT OF ISSUANCE OF NOTIFICATION - NAMECOMPANY ^gt j^f^u^^ CASHINS amp ASSOCINC DATE0 IS
55 CAMBRIDGE STREET bull SUITE 201 bull BURLINGTON MA 01 803 bull TEL 61 7-273-9080 bull FAX fgtl 7-273-9084
CISHINS amp Associates Inc
Industrial Hygirne amp Cmimnmtntal Testing
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Company
LOCATION Salem Acres Superfund Site SL-4 Area
DATES INCLUDED IN SUMMARY T
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87161996 1650 6179444882 CASHINS amp ASSOCIATES
CASHINSamp Associates Inc
WEEKLY HEALTH amp SA7STT PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Coqpanv
LOCATION Sa^am Acras Super fund 5 jte SL-4 Area
DATES INCLUDED IN SUMMARY bull
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53 CAMBRIDGE STREET bull SUTE40I bull BURIJSCTON MA 0803 TfL 61 7-273-908O bull FAX fairo-Jshy
07161996 1658 6179444032 CASHINS S ASSOCIATES PAGE 86
CASHINSamp Associates Inc
MtanW HriHtif A
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT ^ mdash
CLIENT T Ford Company
LOCATION Salem Acraa Suoerfund Sita 5L-4
DATES INCLUDED IN SUMMARY bull
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SUMMARIZED BY FOR CASHINS amp ASSOCIATES INC
55 CAMBRIDGE STREET bullSUITE 201 bull BURllNCTON MA 01803 bull TEL 617-273-9080 bull FAX 617-273-9084
07161996 1650 617944408 CASHING 3 ASSOCIATES PAGE 05
CASHINSamp Associates Inc
fmimnntattl few
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT t T Ford Coimbanv
LOCATION t Salam Acraa Suoarfund Site SL-4 Arlaquoa
DATES INCLUDED IN SUMMARYj pound mdashiffofrshy f
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SUMMARIZ2D BY _ ampampS FOR CASHINS amp ASSOCIATES INC
55 CAMBRIDGE STREET bull SUITE 201 bull BURLINGTON MA 01803 lt TEL 617-273-9080 bull FAX 617-273-9084
CASHIMS amp ASSOCIATES PAGE 04 07161996 1658 6179444032
OVSHINSamp Associates Inc
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Company T
LOCATION Salem AcrM Suoerfund Stta 8L-4 Araa
DATES INCLUDED IN SUMMARY
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SUMMARIZED BY pound FOR CASHINS amp ASSOCIATES INC
55 CAMBRIDGE STREET bull SUITE 201 bull BURUNGTON MA 01803 bull TEL 617-273-9080 bull FAX 617-273-9084
07161996 1658 6179444082 CASHIMS 3 ASSOCIATES PAGE 03
CASHINSamp Associates Inc
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WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT ^
CLIENT T Ford Company t lP ~ ff2-r
LOCATION Sal era Acraa Suplaquorfund Sj-ta 8L-4 Araa
DATES INCLUDED IN SUMMARY
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55 CAMBRIDGE STREET bull SUITE 201 bull 8URUNGTON MA 01803 bull TEL 617-273-9080 bull FAX 617-273-90W
07151996 18 fO 6179444082 CASHINS S ASSOCIATES PAGE 02
CASHINS amp Associates Inc
WBBKLY HEALTH amp SAFETY FLAK COMPLIANCE SUMMARY REPORT
CLIENT T Ford Compapv
LOCATION i Sal am Acrlaquolaquo Suparfund Sita SL-4 Area
DATES INCLUDED IN SUMMARY i bull pound7 mdash
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55 CAMBRIDGE STREET SUITE 201 bull SURtlNCTON MA 01803 TEL 617-273-9080 bull FAX 61 7-273-9084
- barcode 14732
- barcodetext SEMS Doc ID 14732
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- -
--
Oct 17 1995 823PM P02 From LTTS OF Mfl INC PHONE No 617 438 S21S
GRftIN SIZE DISTRIBUTION TEST REPORT C c c e
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90 X
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550 gt
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10
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CRflIM CISC - mm
Test X +3 bull4 GRAVEL bull SflMD bull SILT bull DRY uses LL PI
t 16 00 2Z 3 521 256 SC-SM
SIEVE PERCENT FINCR STEVE PERCENT FINCR Uact on Incrwi nuwtoer ilz ilzi bull flUNSON ST PEABODC
bull bull a 96 3 4 777
15 95 10 714 1 92 e 20 607 Descr pt ion
075 90 40 505 bullSILTY CLAYEY GflNO 0 375 34 50 44 4
100 343
3X1 GRAIN SIZE 200 257
8804D60
gtDia Remarks
xC COEFh 1C1CNT5 UTS OF MASSACHUSETTS INC bull
SS1T to 1 u
Pro jlt-r t No UTS OF naSSACHLKKI lgt IMC Project) CftLCM flCHSCC
5 Richardson Lane
GtoneHam Mft 03 IBB Date 101195 Gamn 1 c- No 44fi1A
Figure 1
From UTS OF Mfl INC PHONE No 517 438 6216 Oct 17 1995 824PM F03
SOT ANALYSIS REPORT FOR NEW LAWN 101195
SOIL AND PLANT TISSUE TESTING LABWEST EXPERIMENT STATIONUNIVERSITY OF MASBACIIUfiFTTr AMHERST MA 01003
LAB NUMBER 3951010-107 BAG NUMBER 23467
DATE BFNT f
SOIL FROM COUNTY SOIL WEIGHT 537 g5cn CROP TURFORASS
UTS OF MASS INC COMMENTS ORGANIC MATTER 6 RICHARDSON LANE STONEHAM MA 02180
SAMPLE ID 4461B
LIMESTONE AND FERTILIZER RECOMMCNDATIONS FOR NEW LAWN CONSTRUCTION
No limestone ia required If peat mooc or similar material ia to be incorporated) see enclosed fact sheet
Fertilizer (per 10OO sq ft) 2 1ba N 2 Ibo P2O5 and O 1 bs KZO
Many fertilizer sources and rates may combine to provide acceptable turfgraes establ iahmont either from seed or aod One or two options baaed on this soil teat follow
Incorporate EITHER a 17-23-6 starter fert111zar at 10 lbs1000 sq ft OR a 30-3-3 lawn fertilizer at 7 1b81000 aq ft plus a 0-45-0 (triple superphosphate) fertilizer at 4 lbs1000 aq ft Hnto the top 3 to 4 inches of soil Retest Bull ona year after turf establishment
PLEASE read the enclosed fact sheets for niora specific Information on fertilization and liming procadurea
SOIL pH 71 NITROGEN NO3-N = Oa ppm NH4-N = 5 ppm BUFFER pH 74 ORGANIC MATTER 72 X (Desirable range 4-10X)
NUTRIENT_LEVELS_PPM_| Low Medium High Very High Phosphorus (P) 8 |XXXXXXXXXXXXX Potaaaium (K) 292 [XXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXX Calcium (Ca) 237S XXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXX Magnesium (Mg) 237 JXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXX
CATION EXCII CAP PERCENT BASE SATURATION MICRONUTRIENT LEVELS 130 Meq100g K= 52 Mg=134 Ca=816 ALL NORMAL
CXTRACTABLE ALUMINUM 41 ppm (Soil ranglaquo 10-250 ppm)
The lead level in thio soil 1s low
COMPUTER PROGRAM5-RECOMMENDATIONRbYOtHIOFPtANT~ampSOILSCI UMASS-AMHERST
Figure 2
TARGET SHEET
THE MATERIAL DESCRIBED BELOW WAS NOT SCANNED BECAUSE
(X) OVERSIZED
() NON-PAPER MEDIA
() OTHER
DESCRIPTION DOC 14732 DRAFT FINAL REMEDIAL CONSTRUCTION REPORT FIGURE 3 TOPOGRAPHIC PLAN SL-4 AREA BOTTOM OF FLY ASH SALEM ACRES SHEET 1 OF 1
THE OMITTED MATERIAL IS AVAILABLE FOR REVIEW BY APPOINTMENT
AT THE EPA NEW ENGLAND SUPERFUND RECORDS CENTER BOSTON MA
TARGET SHEET
THE MATERIAL DESCRIBED BELOW WAS NOT SCANNED BECAUSE
(X) OVERSIZED
() NON-PAPER MEDIA
() OTHER
DESCRIPTION DOC 14732 DRAFT FINAL REMEDIAL CONSTRUCTION REPORT FIGURE 4 TOPOGRAPHIC PLAN SL-4 AREA LIMIT OF REMEDIATION SALEM ACRES SHEET 1OF1
THE OMITTED MATERIAL IS AVAILABLE FOR REVIEW BY APPOINTMENT
AT THE EPA NEW ENGLAND SUPERFUND RECORDS CENTER BOSTON MA
TARGET SHEET
THE MATERIAL DESCRIBED BELOW WAS NOT SCANNED BECAUSE
(X) OVERSIZED
() NON-PAPER MEDIA
() OTHER
DESCRIPTION DOC 14732 DRAFT FINAL REMEDIAL CONSTRUCTION REPORT FIGURE 5 TOPOGRAPHIC PLAN SL-4 AREA AS-BUILT PLAN SALEM ACRES SHEET 1 OF 1
THE OMITTED MATERIAL IS AVAILABLE FOR REVIEW BY APPOINTMENT
AT THE EPA NEW ENGLAND SUPERFUND RECORDS CENTER BOSTON MA
(i)
^mft^m
VIEW OF BARCELONA AVENUE THROUGH ENTRANCE GATE PRECONT RUCTION
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(2)
VIEW OF ACCESS ROAD LOOKING NORTH SL-4 ON LEFT PRECONSTRUCTION
VIEW OF ACCESS ROAD LOOKING NORTH SL-4 ON LEFT DA-1 TO LEFT OF PICKUP TRUCK
PRECONSTRUCTION
(3)
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
O ID a CO z O OHI
CO UJ
OO_l
t CO ii-O
(5)
VIEW OF BOUNDARY BETWEEN SL-4 AND DA-1 LOOKING WEST PRECONSTRUCTION
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(6)
EROSION CONTROLS LOOKING NORTH FROM CORNER OF SL-4SL-5 ADJACENT TO WA-1 PRECONSTRUCTION
(7)
TRUCK LOADING PAD LOOKING NORTHWEST FROM SUPPORT ZONE
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(8)
DECONTAMINATION PAD LOOKING NORTHWEST FROM SUPPORT ZONE
(9)
EXCAVATION OF FLY ASH LOOKING NORTHWEST FROM CRZ NOTE WATER FOR DUST CONTROL
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(10)
VIEW LOOKING WEST AFTER REMOVAL OF FLY ASH NOTE WA-1 BEYOND EROSION CONTROLS
(11)
EXCAVATION OF CONTAMINATED OVERBURDEN LOOKING SOUTH FROM DA-1 BOUNDARY
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(12)
VIEW OF RESTORED SITE LOOKING WEST TOWARD WA-1
0
ltu
wsectbull
D Q
O
O z ^ O O_J LJJ
Q LJJ a o te LJJ
eg 3
(14)
VIEW OF RESTORED SITE LOOKING NORTH TOWARD DA-1 ALONG ACCESS ROAD
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(15)
gtbull bdquobdquo -
VIEW OF RESTORED SITE LOOKING SOUTH TOWARD SL-5
iu O
of bullo
01 u I ltO
w
o B ltabulls to 10
3
I Q Z
O m ^mdash
i sect^^ nu0 (- co^gtW IO - z zilaquo O O 5gl
oLU uj
V) LUo a o LU
(17)
VIEW OF RESTORED SITE ON DA-1 SJDE OF FENCE - LOOKING ST
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(18)
VIEW OF RESTORED SITE ON DA-1 SIDE OF FENCE - LOOKING WEST SL-4 ON RIGHT
APPENDIX A
ANALYTICAL RESULTS FOR
PONDED WATER
110795 1638 copy617 890 3883 TMA-WALTHAM ] 002007
PRELIMINARY REPORT UNAUDITED RESULTS
Thenno Analytical 300 Second Avenue PO Box 521 Waltham HA 02254
Attn Client Services Phone (617) 890-7200
Cashins amp Associates Order S5-11-034 55 Cambridge Street Date 110795 1522 Burlington HA 01803 Work ID Salem Acres Water
Date Received 110295 Attn Bob Cashins Date Completed
Purchase Order NA Invoice Number Client Code CASHINS
SAMPLE IDENTIFICATION
Sample Sample Number Description 01 11019S-924-01A
Sample Number 04
Sample Description
110195-9Z4-01D 02 110195-924-01B 05 110195-924-01E 03 110195-924-01C
Certified By
110795 1638 copy617 890 3883 TMA-WALTHAM 003007
PRELIMINARY REPORT UNAUDITED RESULTS
Order f S5-11-034 Thermo Analytical Page 2 110795 1522 TEST RESULTS BY SAHPLE
Test Description Volatile Organics- Aqueous Method EPA_8240 Test Code Collected 110195 02-00 Category WATER
DATE INJECTED 110695 DILUTION FACTOR 100 All results reported 1n ugL
COMPOUND RESULT DET LIMIT COMPOUND RESULT
Chloromethane U 10 Broroodi chl oromethane U Vinyl Chloride U 10 2-Chloroethyl Vinyl Ether U
Bromxnethane U 10 4-dethyl -2-pentanone U Chloroethane U 10 c1 3-1 3-Di chl oropropene U
Trichlorofluoronwthane U 50 Tol uene U Acetone 17 10 trans-1 3-Di chl oropropene LI
11-Oichloroethene U 50 11 2-Tri chl oroethane J Carbon Dlsulfide U 50 2-Hexanone U
Methyl ene Chloride U 50 Tetrachl oroethene U 12-Oichloroethene (total) U 50 D1 bromochl oromethane U
11-01 Chloroethane U 50 Chlorobenzene U Vinyl Acetate U 10 Ethyl benzene U
2-Butanone U 10 in and p-Xylene U Chloroform U 50 o-Xylene U
111-Tri Chloroethane U 50 Styrene U Carbon Tetrachlortde U 50 Broraoform U
Benzene U 50 112 2-Tat rachl oroethane U 12-01 Chloroethane U 50 1 3-01 chl orobenzene U
Trichloroethene U 50 I 4-Di chl orobenzene U 12-Dichloropropane U 50 12-01 chl orobenzene U
SURROGATE STANDARDS RESULT LEVEL X RECOVERY
12-Dichloroethane-D4 52 50 104 Toluene-08 47 50 94
l-Bromo-4-fluorobenzene 56 50 112
NOTES AND DEFINITIONS FOR THIS REPORT U =bull Undetected at stated detection limit
VOAJI
OET LIMIT
50 50
10 50 50 50 50 10
5 0 50 5 0 5 0 50 50 50 50 50 50 50 50
110795 1639 copy617 890 3883 TMA-WALTHAM copy004007
PRELIMINARY REPORT UNAUDITED RESULTS
Order t S5-11-034 Thermo Analytical Page 4 110795 1522 TEST RESULTS BY SAMPLE
ianple Description 110195-924-010 Lab No 04A Test Description RCRA Metals 1n Water Method SW846 Test Code
Collected 110195 0200 Category WATER
METAL RESULT DETECTION LIMIT METAL RESULT DETECTION LIMIT
Ag Silver U 10 As Arsenic 870 50
Ba Bar inn B69 10 Pb Lead U 50
Cd Cadmium U 50 Se Sel en1 um Z15 50
Cr Chromi um U 20 Hg Mercury U 020
NOTES AND DEFINITIONS FOR THIS REPORT All results reported in ugL U gt Undetected at stated detection limit
110795 1640 Q617 890 3883 TMA-WALTHAM 0005007
PRELIMINARY REPORT UNAUDITED RESULTS
Order S5-11-034 Thermo Analytical Page 5 110795 1522 REGULAR TEST RESULTS BY TEST
Chemical Oxygen Demand Mlnimun Maximum Method EPA600 4101
Sap Sample Description Result Units Limit Prepared Analyzed By 05A 110195-924-01E 64 bullgL 50 110395 110395 JD
Petroleum Hydrocarbons-H20 Minimum Maximum Method EPA600 4181
Samp Sample Description Result Units Limit Prepared Analyzed By 01A 110195-924-01A 108 mgL 050 110395 110395 JO
110795 1640 reg617 890 3883 TMA-WALTHAM copy006007
PRELIMINARY REPORT UNAUDITED RESULTS
Order I S5-11-034 Therm Analytical Page 6 110795 1522 TEST METHODOLOGIES
USEPA Test Methods for Evaluating Solid Wastes (SUS46 Third Edition) Method 7470 - Preparation of water for Mercury analysis
USEPA Test Methods for Evaluating Solid Vastes (SW846 Third Edition) Method 3010 - Add digestion of aqueous samples and extracts for total metals for analysis by Flame Atomic Absorption Spectroscopy or Inductively Coupled Plasma Spectroscopy
USEPA Test Methods for Evaluating Solid Vastes (SWB46 Third Edition Method 8270 mdash Gas ChroroatographyMass Spectrometry for PAHs
Volatile Organics in Water - Hazardous Substance List
SV846 Method 8240 - Modified
Test Methods for Evaluating Solid Waste SU-846 US EPA Office of Solid Waste and Emergency Response Washington 3rd Edition
Aqueous sanples are analyzed in accordance with Method 8240 using a purge and trap technique followed by 64s ChromatographyMass Spectroscopy
Quality assurance procedures for GCMS Include daily tuning and calibration of the mass spectrometer and the use of surrogate standards in each sample to monitor method performance Quantitatton is performed by the Internal standard method Analysis of blanks duplicate samples and standards are run frequently as further quality assurance procedures
USEPA Test Methods for Evaluating Solid Wastes (SW846 Third Edition) Method 3S10 mdash Separatory Funnel Liquid-Liquid Extraction
EPA-6004-79-020 - Chemical Oxygen Demand - Titrimetric Mid-Level Method 4101
EPA6004-79-020 - Petroleum Hydrocarbons 1n Water Total Recoverable Method 4181 (Spectrophotometric Infrared)
110795 1641 copy617 890 3883 TMA-WALTHAM copy007007
APPENDIX B
QUANTITY SURVEY DOCUMENTATION
TFMORAN INC Surveying - Engineering - Land Planning SoilsWetlands Mapping - Landscape Architecture
January 15 1996
Mr Jack Enos Vice President TFord Company Inc 118 Tenney Street Georgetown MA 01833
RE Survey Results - Salem Acres - SL4 Area Salem Massachusetts
Dear Jack
This letter amends the letter of December 13 1995 per our review last week
TFMoran Inc performed topographic surveys at the Salem Acres site on April 21 1994 for GEI Consultants prior to removal of material and for TFord Company on October 18 1995 after the removal of material The survey data from the original survey in 1994 was adjusted thirty feet higher to correct for a datum difference from current site datum This was due to the original reporting of the Site Benchmark (TP34) elevation as 11464 rather than 14464 which is the correct elevation
Once both topographic surfaces were on the site datum the raw cut volume was obtained by Eaglepoint (Volumes Module) Software utilizing the prismoidal method comparing the two surfaces For reference please see the attached topographic plan which superimposes the October 15 1995 contours (dark lines) over the April 21 1994 contours The volume is based on the intersection of the two surfaces Also it was noted that stock piles of material did exist on site which were not surveyed at the time
The final raw cut volume arrived at by the above methods is 12749 Cubic Yards
In November and December of 1995 the site was resurveyed to locate the area of exposed ledge at the site The results of this survey are shown on the attached topographic worksheet dated November 3 1995 and last revised January 15 1996 The results of the survey indicate the total site area to be 50860 sq ft or 117 acres The total area of exposed ledge surveyed is 19990 sq ft or 46 acres If you have any questions regarding the above call me directly Thank you
Sincerely
John W Myhaver Jr ^_ Field Operations Manager
Enclosure ItorLltr
Route 101 Bedford NH 03110 Phone (603) 472-4488 FAX (603) 472-9747
APPENDIX C
HEALTH AND SAFETY PHASE-OUT REPORT
HEALTH AND SAFETY PHASE-OUT REPORT SALEM ACRES SL-4 AREA
Introduction
During remediation work on SL-4 Health and Safety Monitoring was performed Cashins amp Associates Inc of Reading MA performed the following work as a subcontractor to TFCI
1) Preparation of a site-specific Health and Safety Plan (dated September 1 1995)
2) Provide a Field TechnicianIndustrial Hygienist to serve as Site Safety and Health Officer (SSHO) and to conduct air and noise monitoring
3) Provide a Certified Industrial Hygienist to review Health and Safety and to conduct site specific training (record of training included at end of Appendix C)
4) Collect 8-hour air samples for worker exposure and ambient air at the Barcelona Avenue gate Arrange for analysis of the samples and report results
5) Prepare daily and weekly Health and Safety reports
6) Prepare a Health and Safety Phase-Out Report
In general the following health and safety practices were followed
1) All workers wore hard hats safety glasses work boots gloves and hearing protection as minimum level PPE
2) When working in the exclusion zone workers wore in addition to above tyvek rubber overboots and rubber coated gloves When dust was a potential concern an industrial grade dustmist mask was also worn This level of PPE was considered Level D modified
3) Workers leaving the exclusion zone removed PPE (tyveks gloves boots and masks) in the support zone and either disposed of the items or decontaminated them
4) Workers andor visitors without 40-hour OSHA training were not permitted to enter the exclusion zone
Attached is a report prepared by Cashins amp Associates along with weekly Health and Safety Summary Reports prepared by the Field Hygienist In summary the air monitoring results indicate no levels exceeding the applicable exposure guidelines except one instance
During excavation of contaminated overburden in the northwest comer of the site an area of VOC contaminated soil was encountered Total VOCs levels measured using a PID exceeded the action level established in the Health and Safety Plan The SSHO advised TFCI to upgrade to Level C PPE in order to backfill the excavation in this area TFCI equipment operator upgraded and backfilled the area The SSHO in consultation with the Cashins CIH advised TFCI to avoid work in this area until the contaminants were characterized GEI sampled the material for waste characterization analysis and provided the results to TFCI Based on the results an action level was established by the CIH for the specific contaminants found Further PID measurements indicated levels below the new action level and work was resumed
The noise monitoring indicated that the noise level at the Barcelona Avenue gate was not exceeded Only one instance of excess noise level in the work zone was recorded (10 db(a) above the ambient noise level or 85 db(a)) Workers wore hearing protection in this instance
mdash 07171996 1601 6179444032 CASHIMS S ASSOCIATES PAGE 02
CASHINS amp Associates Inc
ItxhalrM Hy-gifnr A Invtronmtnltl Tttling
July 17 1996
Mr Jack Enos T Ford Company Inc USTenney Street Georgetown MA 01833
Dear Jack
The Site Safety and Health Officer (SSHO) from Cashing amp Associates Inc performed daily inspections of the SL-4 area Salem Acres Superfund Site between 9595 and 12195 in accordance with the Health amp Safety Plan (HSP) for the site Daily inspection logs were submitted every day No accidentsincidents were reported during the work period
In accordance with the Health amp Safety Plan the SSHO performed daily air and noise monitoring at the site during Ac project Samples were collected for metals (lead beryllium chromium arsenic) and Polynuclear Aromatic Hydrocarbons (PAHs) at the site perimeter and for workers exposure determination Coal Tar Pitch Volatiles (a benzene soluble extractables) were also used to determine the workers exposure to PAH compounds Coal Tar Pitch Volatiles (CTPV) were analyzed using OSHA 58 Method If CTPV levels oq personal samples exceed the site criteria of 02 ragm3 the sample was submitted for PAHs analysis All air samples on the site perimeter were analyzed for PAH compounds
Site monitoring air sample collection and results report were done under the supervision of a Certified Industrial Hygienist
Full shift personal worker exposure samples were collected once a week Ambient air samples were collected at the Barcelona Avenue gate about 20 feet to the west of the site gate to determine if site contaminants were migrating off site The ambient air samples were also collected once a week during the project except on rainy days and days without work with contaminated soil
All air samples were analyzed by the American Industrial Hygiene Association accredited ESA Laboratories Inc using the following methods PAHs - NIOSH 5515 Lead - NIOSH 7082 Beryllium - NIOSH 7102 Chromium - NIOSH 7024 Arsenic - NIOSH 7900 Coal Tar Pitch Volatiles - OSHA 58 All methods used are accepted by the industrial hygiene community for 8-hour exposure assessment EPA methods are usually used for ambient air measurements
CRErORTTFOmiOO
80 Mam Street bull Reading MA 01867 bull Phone- 61 7-944-4060 bull Fax 61 7-944-4082
07171996 1601 6179444032 CASHIMS amp ASSOCIATES PAGE 03
The results of air samples for metals and PAHs are presented in Table No 1
All concentrations of metals and PAHs at the site perimeter (Barcelona Avenue) and active work zones were below the OSHA Permissible Exposure Limits (PEL) and the American Conference of Governmental Industrial Hygicnists Threshold Limit Value (ACGIH TLV) Two personal samples collected on October 19 and October 23rd showed Coal Tar Pitch Volatiles (CTPV) results above OSHA PEL and AIHA TLV limits Both samples were resubmittcd to the lab for further analysis to determine if PAH compounds are present because the CTPV results were above site criteria
The results of the PAH concentrations for the personal sample on Mark Goodwin on October 19 1995 during excavation and washing trucks and for the personal sample on Ron Maker on October 23 1995 during excavating and cleaning rocks by compressed air were below OSHA PEL and ACGIH TLV limits
The SSHO performed noise monitoring according to the HSP at the exclusion zone and at the Barcelona Avenue site perimeter fence A Dupont sound level meter was used for noise monitoring The noise level in the exclusion zone during all operations except one did not exceed the on site criteria of 85 dB(a) During a short time when the air compressor had been used to clean rocks the sound level in the exclusion zone next to the air compressor did exceed 85 dB(a) Ear protection devices were worn by the workers during that operation At no time did the noise level at the Barcelona Avenue site perimeter exceed 10 dB(a) above the ambient noise level or 85 dB(a)
The SSHO performed total dust monitoring on a daily basis during the project at the site perimeter downwind of work location and at the site gate using a Miniram real time dust meter The summary of dust monitoring is presented in Table No 2 Total dust concentrations on site and off site did not exceed site criteria of 1 mgm3 and the action level of 05 nigny1
The summary of air monitoring for Volatile Organic Compounds (VOC) is presented in Table No 3 VOC concentrations in the working area did not exceed the on site criteria of 5 ppm in a breathing zone VOC concentrations on the site perimeter did not exceed real time off site criteria of 2 ppm
Five detail reports with results of air sampling were submitted during the project period
Sincerely Cashins amp Associates Inc
Evelina Vaughan Industrial Hygieflfst
CASHINS amp ASSOCIATES Inc
80 Mam Street bull Reading MA 01867 bull Phone61 7-944-4060 bull Fax 617-944-4082
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DATES INCLUDED IN SUMMARY
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WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
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CASHINS amp Associates Inc
WBBKLY HEALTH amp SAFETY FLAK COMPLIANCE SUMMARY REPORT
CLIENT T Ford Compapv
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- barcode 14732
- barcodetext SEMS Doc ID 14732
![Page 15: SALEM ACRES SUPERFUND SITE SALEM, MA ...The truck loading pa d consisted of a crushed stone are sea t up along the east sid e o f SL-4 adjacent to the access road A. row of concrete](https://reader036.vdocuments.us/reader036/viewer/2022070114/60729b840fec4e6b4d136a16/html5/thumbnails/15.jpg)
From UTS OF Mfl INC PHONE No 517 438 6216 Oct 17 1995 824PM F03
SOT ANALYSIS REPORT FOR NEW LAWN 101195
SOIL AND PLANT TISSUE TESTING LABWEST EXPERIMENT STATIONUNIVERSITY OF MASBACIIUfiFTTr AMHERST MA 01003
LAB NUMBER 3951010-107 BAG NUMBER 23467
DATE BFNT f
SOIL FROM COUNTY SOIL WEIGHT 537 g5cn CROP TURFORASS
UTS OF MASS INC COMMENTS ORGANIC MATTER 6 RICHARDSON LANE STONEHAM MA 02180
SAMPLE ID 4461B
LIMESTONE AND FERTILIZER RECOMMCNDATIONS FOR NEW LAWN CONSTRUCTION
No limestone ia required If peat mooc or similar material ia to be incorporated) see enclosed fact sheet
Fertilizer (per 10OO sq ft) 2 1ba N 2 Ibo P2O5 and O 1 bs KZO
Many fertilizer sources and rates may combine to provide acceptable turfgraes establ iahmont either from seed or aod One or two options baaed on this soil teat follow
Incorporate EITHER a 17-23-6 starter fert111zar at 10 lbs1000 sq ft OR a 30-3-3 lawn fertilizer at 7 1b81000 aq ft plus a 0-45-0 (triple superphosphate) fertilizer at 4 lbs1000 aq ft Hnto the top 3 to 4 inches of soil Retest Bull ona year after turf establishment
PLEASE read the enclosed fact sheets for niora specific Information on fertilization and liming procadurea
SOIL pH 71 NITROGEN NO3-N = Oa ppm NH4-N = 5 ppm BUFFER pH 74 ORGANIC MATTER 72 X (Desirable range 4-10X)
NUTRIENT_LEVELS_PPM_| Low Medium High Very High Phosphorus (P) 8 |XXXXXXXXXXXXX Potaaaium (K) 292 [XXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXX Calcium (Ca) 237S XXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXX Magnesium (Mg) 237 JXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXXX
CATION EXCII CAP PERCENT BASE SATURATION MICRONUTRIENT LEVELS 130 Meq100g K= 52 Mg=134 Ca=816 ALL NORMAL
CXTRACTABLE ALUMINUM 41 ppm (Soil ranglaquo 10-250 ppm)
The lead level in thio soil 1s low
COMPUTER PROGRAM5-RECOMMENDATIONRbYOtHIOFPtANT~ampSOILSCI UMASS-AMHERST
Figure 2
TARGET SHEET
THE MATERIAL DESCRIBED BELOW WAS NOT SCANNED BECAUSE
(X) OVERSIZED
() NON-PAPER MEDIA
() OTHER
DESCRIPTION DOC 14732 DRAFT FINAL REMEDIAL CONSTRUCTION REPORT FIGURE 3 TOPOGRAPHIC PLAN SL-4 AREA BOTTOM OF FLY ASH SALEM ACRES SHEET 1 OF 1
THE OMITTED MATERIAL IS AVAILABLE FOR REVIEW BY APPOINTMENT
AT THE EPA NEW ENGLAND SUPERFUND RECORDS CENTER BOSTON MA
TARGET SHEET
THE MATERIAL DESCRIBED BELOW WAS NOT SCANNED BECAUSE
(X) OVERSIZED
() NON-PAPER MEDIA
() OTHER
DESCRIPTION DOC 14732 DRAFT FINAL REMEDIAL CONSTRUCTION REPORT FIGURE 4 TOPOGRAPHIC PLAN SL-4 AREA LIMIT OF REMEDIATION SALEM ACRES SHEET 1OF1
THE OMITTED MATERIAL IS AVAILABLE FOR REVIEW BY APPOINTMENT
AT THE EPA NEW ENGLAND SUPERFUND RECORDS CENTER BOSTON MA
TARGET SHEET
THE MATERIAL DESCRIBED BELOW WAS NOT SCANNED BECAUSE
(X) OVERSIZED
() NON-PAPER MEDIA
() OTHER
DESCRIPTION DOC 14732 DRAFT FINAL REMEDIAL CONSTRUCTION REPORT FIGURE 5 TOPOGRAPHIC PLAN SL-4 AREA AS-BUILT PLAN SALEM ACRES SHEET 1 OF 1
THE OMITTED MATERIAL IS AVAILABLE FOR REVIEW BY APPOINTMENT
AT THE EPA NEW ENGLAND SUPERFUND RECORDS CENTER BOSTON MA
(i)
^mft^m
VIEW OF BARCELONA AVENUE THROUGH ENTRANCE GATE PRECONT RUCTION
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(2)
VIEW OF ACCESS ROAD LOOKING NORTH SL-4 ON LEFT PRECONSTRUCTION
VIEW OF ACCESS ROAD LOOKING NORTH SL-4 ON LEFT DA-1 TO LEFT OF PICKUP TRUCK
PRECONSTRUCTION
(3)
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
O ID a CO z O OHI
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(5)
VIEW OF BOUNDARY BETWEEN SL-4 AND DA-1 LOOKING WEST PRECONSTRUCTION
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(6)
EROSION CONTROLS LOOKING NORTH FROM CORNER OF SL-4SL-5 ADJACENT TO WA-1 PRECONSTRUCTION
(7)
TRUCK LOADING PAD LOOKING NORTHWEST FROM SUPPORT ZONE
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(8)
DECONTAMINATION PAD LOOKING NORTHWEST FROM SUPPORT ZONE
(9)
EXCAVATION OF FLY ASH LOOKING NORTHWEST FROM CRZ NOTE WATER FOR DUST CONTROL
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(10)
VIEW LOOKING WEST AFTER REMOVAL OF FLY ASH NOTE WA-1 BEYOND EROSION CONTROLS
(11)
EXCAVATION OF CONTAMINATED OVERBURDEN LOOKING SOUTH FROM DA-1 BOUNDARY
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(12)
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VIEW OF RESTORED SITE ON DA-1 SIDE OF FENCE - LOOKING WEST SL-4 ON RIGHT
APPENDIX A
ANALYTICAL RESULTS FOR
PONDED WATER
110795 1638 copy617 890 3883 TMA-WALTHAM ] 002007
PRELIMINARY REPORT UNAUDITED RESULTS
Thenno Analytical 300 Second Avenue PO Box 521 Waltham HA 02254
Attn Client Services Phone (617) 890-7200
Cashins amp Associates Order S5-11-034 55 Cambridge Street Date 110795 1522 Burlington HA 01803 Work ID Salem Acres Water
Date Received 110295 Attn Bob Cashins Date Completed
Purchase Order NA Invoice Number Client Code CASHINS
SAMPLE IDENTIFICATION
Sample Sample Number Description 01 11019S-924-01A
Sample Number 04
Sample Description
110195-9Z4-01D 02 110195-924-01B 05 110195-924-01E 03 110195-924-01C
Certified By
110795 1638 copy617 890 3883 TMA-WALTHAM 003007
PRELIMINARY REPORT UNAUDITED RESULTS
Order f S5-11-034 Thermo Analytical Page 2 110795 1522 TEST RESULTS BY SAHPLE
Test Description Volatile Organics- Aqueous Method EPA_8240 Test Code Collected 110195 02-00 Category WATER
DATE INJECTED 110695 DILUTION FACTOR 100 All results reported 1n ugL
COMPOUND RESULT DET LIMIT COMPOUND RESULT
Chloromethane U 10 Broroodi chl oromethane U Vinyl Chloride U 10 2-Chloroethyl Vinyl Ether U
Bromxnethane U 10 4-dethyl -2-pentanone U Chloroethane U 10 c1 3-1 3-Di chl oropropene U
Trichlorofluoronwthane U 50 Tol uene U Acetone 17 10 trans-1 3-Di chl oropropene LI
11-Oichloroethene U 50 11 2-Tri chl oroethane J Carbon Dlsulfide U 50 2-Hexanone U
Methyl ene Chloride U 50 Tetrachl oroethene U 12-Oichloroethene (total) U 50 D1 bromochl oromethane U
11-01 Chloroethane U 50 Chlorobenzene U Vinyl Acetate U 10 Ethyl benzene U
2-Butanone U 10 in and p-Xylene U Chloroform U 50 o-Xylene U
111-Tri Chloroethane U 50 Styrene U Carbon Tetrachlortde U 50 Broraoform U
Benzene U 50 112 2-Tat rachl oroethane U 12-01 Chloroethane U 50 1 3-01 chl orobenzene U
Trichloroethene U 50 I 4-Di chl orobenzene U 12-Dichloropropane U 50 12-01 chl orobenzene U
SURROGATE STANDARDS RESULT LEVEL X RECOVERY
12-Dichloroethane-D4 52 50 104 Toluene-08 47 50 94
l-Bromo-4-fluorobenzene 56 50 112
NOTES AND DEFINITIONS FOR THIS REPORT U =bull Undetected at stated detection limit
VOAJI
OET LIMIT
50 50
10 50 50 50 50 10
5 0 50 5 0 5 0 50 50 50 50 50 50 50 50
110795 1639 copy617 890 3883 TMA-WALTHAM copy004007
PRELIMINARY REPORT UNAUDITED RESULTS
Order t S5-11-034 Thermo Analytical Page 4 110795 1522 TEST RESULTS BY SAMPLE
ianple Description 110195-924-010 Lab No 04A Test Description RCRA Metals 1n Water Method SW846 Test Code
Collected 110195 0200 Category WATER
METAL RESULT DETECTION LIMIT METAL RESULT DETECTION LIMIT
Ag Silver U 10 As Arsenic 870 50
Ba Bar inn B69 10 Pb Lead U 50
Cd Cadmium U 50 Se Sel en1 um Z15 50
Cr Chromi um U 20 Hg Mercury U 020
NOTES AND DEFINITIONS FOR THIS REPORT All results reported in ugL U gt Undetected at stated detection limit
110795 1640 Q617 890 3883 TMA-WALTHAM 0005007
PRELIMINARY REPORT UNAUDITED RESULTS
Order S5-11-034 Thermo Analytical Page 5 110795 1522 REGULAR TEST RESULTS BY TEST
Chemical Oxygen Demand Mlnimun Maximum Method EPA600 4101
Sap Sample Description Result Units Limit Prepared Analyzed By 05A 110195-924-01E 64 bullgL 50 110395 110395 JD
Petroleum Hydrocarbons-H20 Minimum Maximum Method EPA600 4181
Samp Sample Description Result Units Limit Prepared Analyzed By 01A 110195-924-01A 108 mgL 050 110395 110395 JO
110795 1640 reg617 890 3883 TMA-WALTHAM copy006007
PRELIMINARY REPORT UNAUDITED RESULTS
Order I S5-11-034 Therm Analytical Page 6 110795 1522 TEST METHODOLOGIES
USEPA Test Methods for Evaluating Solid Wastes (SUS46 Third Edition) Method 7470 - Preparation of water for Mercury analysis
USEPA Test Methods for Evaluating Solid Vastes (SW846 Third Edition) Method 3010 - Add digestion of aqueous samples and extracts for total metals for analysis by Flame Atomic Absorption Spectroscopy or Inductively Coupled Plasma Spectroscopy
USEPA Test Methods for Evaluating Solid Vastes (SWB46 Third Edition Method 8270 mdash Gas ChroroatographyMass Spectrometry for PAHs
Volatile Organics in Water - Hazardous Substance List
SV846 Method 8240 - Modified
Test Methods for Evaluating Solid Waste SU-846 US EPA Office of Solid Waste and Emergency Response Washington 3rd Edition
Aqueous sanples are analyzed in accordance with Method 8240 using a purge and trap technique followed by 64s ChromatographyMass Spectroscopy
Quality assurance procedures for GCMS Include daily tuning and calibration of the mass spectrometer and the use of surrogate standards in each sample to monitor method performance Quantitatton is performed by the Internal standard method Analysis of blanks duplicate samples and standards are run frequently as further quality assurance procedures
USEPA Test Methods for Evaluating Solid Wastes (SW846 Third Edition) Method 3S10 mdash Separatory Funnel Liquid-Liquid Extraction
EPA-6004-79-020 - Chemical Oxygen Demand - Titrimetric Mid-Level Method 4101
EPA6004-79-020 - Petroleum Hydrocarbons 1n Water Total Recoverable Method 4181 (Spectrophotometric Infrared)
110795 1641 copy617 890 3883 TMA-WALTHAM copy007007
APPENDIX B
QUANTITY SURVEY DOCUMENTATION
TFMORAN INC Surveying - Engineering - Land Planning SoilsWetlands Mapping - Landscape Architecture
January 15 1996
Mr Jack Enos Vice President TFord Company Inc 118 Tenney Street Georgetown MA 01833
RE Survey Results - Salem Acres - SL4 Area Salem Massachusetts
Dear Jack
This letter amends the letter of December 13 1995 per our review last week
TFMoran Inc performed topographic surveys at the Salem Acres site on April 21 1994 for GEI Consultants prior to removal of material and for TFord Company on October 18 1995 after the removal of material The survey data from the original survey in 1994 was adjusted thirty feet higher to correct for a datum difference from current site datum This was due to the original reporting of the Site Benchmark (TP34) elevation as 11464 rather than 14464 which is the correct elevation
Once both topographic surfaces were on the site datum the raw cut volume was obtained by Eaglepoint (Volumes Module) Software utilizing the prismoidal method comparing the two surfaces For reference please see the attached topographic plan which superimposes the October 15 1995 contours (dark lines) over the April 21 1994 contours The volume is based on the intersection of the two surfaces Also it was noted that stock piles of material did exist on site which were not surveyed at the time
The final raw cut volume arrived at by the above methods is 12749 Cubic Yards
In November and December of 1995 the site was resurveyed to locate the area of exposed ledge at the site The results of this survey are shown on the attached topographic worksheet dated November 3 1995 and last revised January 15 1996 The results of the survey indicate the total site area to be 50860 sq ft or 117 acres The total area of exposed ledge surveyed is 19990 sq ft or 46 acres If you have any questions regarding the above call me directly Thank you
Sincerely
John W Myhaver Jr ^_ Field Operations Manager
Enclosure ItorLltr
Route 101 Bedford NH 03110 Phone (603) 472-4488 FAX (603) 472-9747
APPENDIX C
HEALTH AND SAFETY PHASE-OUT REPORT
HEALTH AND SAFETY PHASE-OUT REPORT SALEM ACRES SL-4 AREA
Introduction
During remediation work on SL-4 Health and Safety Monitoring was performed Cashins amp Associates Inc of Reading MA performed the following work as a subcontractor to TFCI
1) Preparation of a site-specific Health and Safety Plan (dated September 1 1995)
2) Provide a Field TechnicianIndustrial Hygienist to serve as Site Safety and Health Officer (SSHO) and to conduct air and noise monitoring
3) Provide a Certified Industrial Hygienist to review Health and Safety and to conduct site specific training (record of training included at end of Appendix C)
4) Collect 8-hour air samples for worker exposure and ambient air at the Barcelona Avenue gate Arrange for analysis of the samples and report results
5) Prepare daily and weekly Health and Safety reports
6) Prepare a Health and Safety Phase-Out Report
In general the following health and safety practices were followed
1) All workers wore hard hats safety glasses work boots gloves and hearing protection as minimum level PPE
2) When working in the exclusion zone workers wore in addition to above tyvek rubber overboots and rubber coated gloves When dust was a potential concern an industrial grade dustmist mask was also worn This level of PPE was considered Level D modified
3) Workers leaving the exclusion zone removed PPE (tyveks gloves boots and masks) in the support zone and either disposed of the items or decontaminated them
4) Workers andor visitors without 40-hour OSHA training were not permitted to enter the exclusion zone
Attached is a report prepared by Cashins amp Associates along with weekly Health and Safety Summary Reports prepared by the Field Hygienist In summary the air monitoring results indicate no levels exceeding the applicable exposure guidelines except one instance
During excavation of contaminated overburden in the northwest comer of the site an area of VOC contaminated soil was encountered Total VOCs levels measured using a PID exceeded the action level established in the Health and Safety Plan The SSHO advised TFCI to upgrade to Level C PPE in order to backfill the excavation in this area TFCI equipment operator upgraded and backfilled the area The SSHO in consultation with the Cashins CIH advised TFCI to avoid work in this area until the contaminants were characterized GEI sampled the material for waste characterization analysis and provided the results to TFCI Based on the results an action level was established by the CIH for the specific contaminants found Further PID measurements indicated levels below the new action level and work was resumed
The noise monitoring indicated that the noise level at the Barcelona Avenue gate was not exceeded Only one instance of excess noise level in the work zone was recorded (10 db(a) above the ambient noise level or 85 db(a)) Workers wore hearing protection in this instance
mdash 07171996 1601 6179444032 CASHIMS S ASSOCIATES PAGE 02
CASHINS amp Associates Inc
ItxhalrM Hy-gifnr A Invtronmtnltl Tttling
July 17 1996
Mr Jack Enos T Ford Company Inc USTenney Street Georgetown MA 01833
Dear Jack
The Site Safety and Health Officer (SSHO) from Cashing amp Associates Inc performed daily inspections of the SL-4 area Salem Acres Superfund Site between 9595 and 12195 in accordance with the Health amp Safety Plan (HSP) for the site Daily inspection logs were submitted every day No accidentsincidents were reported during the work period
In accordance with the Health amp Safety Plan the SSHO performed daily air and noise monitoring at the site during Ac project Samples were collected for metals (lead beryllium chromium arsenic) and Polynuclear Aromatic Hydrocarbons (PAHs) at the site perimeter and for workers exposure determination Coal Tar Pitch Volatiles (a benzene soluble extractables) were also used to determine the workers exposure to PAH compounds Coal Tar Pitch Volatiles (CTPV) were analyzed using OSHA 58 Method If CTPV levels oq personal samples exceed the site criteria of 02 ragm3 the sample was submitted for PAHs analysis All air samples on the site perimeter were analyzed for PAH compounds
Site monitoring air sample collection and results report were done under the supervision of a Certified Industrial Hygienist
Full shift personal worker exposure samples were collected once a week Ambient air samples were collected at the Barcelona Avenue gate about 20 feet to the west of the site gate to determine if site contaminants were migrating off site The ambient air samples were also collected once a week during the project except on rainy days and days without work with contaminated soil
All air samples were analyzed by the American Industrial Hygiene Association accredited ESA Laboratories Inc using the following methods PAHs - NIOSH 5515 Lead - NIOSH 7082 Beryllium - NIOSH 7102 Chromium - NIOSH 7024 Arsenic - NIOSH 7900 Coal Tar Pitch Volatiles - OSHA 58 All methods used are accepted by the industrial hygiene community for 8-hour exposure assessment EPA methods are usually used for ambient air measurements
CRErORTTFOmiOO
80 Mam Street bull Reading MA 01867 bull Phone- 61 7-944-4060 bull Fax 61 7-944-4082
07171996 1601 6179444032 CASHIMS amp ASSOCIATES PAGE 03
The results of air samples for metals and PAHs are presented in Table No 1
All concentrations of metals and PAHs at the site perimeter (Barcelona Avenue) and active work zones were below the OSHA Permissible Exposure Limits (PEL) and the American Conference of Governmental Industrial Hygicnists Threshold Limit Value (ACGIH TLV) Two personal samples collected on October 19 and October 23rd showed Coal Tar Pitch Volatiles (CTPV) results above OSHA PEL and AIHA TLV limits Both samples were resubmittcd to the lab for further analysis to determine if PAH compounds are present because the CTPV results were above site criteria
The results of the PAH concentrations for the personal sample on Mark Goodwin on October 19 1995 during excavation and washing trucks and for the personal sample on Ron Maker on October 23 1995 during excavating and cleaning rocks by compressed air were below OSHA PEL and ACGIH TLV limits
The SSHO performed noise monitoring according to the HSP at the exclusion zone and at the Barcelona Avenue site perimeter fence A Dupont sound level meter was used for noise monitoring The noise level in the exclusion zone during all operations except one did not exceed the on site criteria of 85 dB(a) During a short time when the air compressor had been used to clean rocks the sound level in the exclusion zone next to the air compressor did exceed 85 dB(a) Ear protection devices were worn by the workers during that operation At no time did the noise level at the Barcelona Avenue site perimeter exceed 10 dB(a) above the ambient noise level or 85 dB(a)
The SSHO performed total dust monitoring on a daily basis during the project at the site perimeter downwind of work location and at the site gate using a Miniram real time dust meter The summary of dust monitoring is presented in Table No 2 Total dust concentrations on site and off site did not exceed site criteria of 1 mgm3 and the action level of 05 nigny1
The summary of air monitoring for Volatile Organic Compounds (VOC) is presented in Table No 3 VOC concentrations in the working area did not exceed the on site criteria of 5 ppm in a breathing zone VOC concentrations on the site perimeter did not exceed real time off site criteria of 2 ppm
Five detail reports with results of air sampling were submitted during the project period
Sincerely Cashins amp Associates Inc
Evelina Vaughan Industrial Hygieflfst
CASHINS amp ASSOCIATES Inc
80 Mam Street bull Reading MA 01867 bull Phone61 7-944-4060 bull Fax 617-944-4082
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89111995 1023 6172733(384 CASHINS ASSOCIATES PAGE 01
CASHINS amp Associates inc
Ifxtuitral Hygltne A fnvironmtnltt Tuning
W3SXLY HBALTH amp SAFETY PLAN COMPLIANCE SUMMARY R3PORT
CLIENT T foyd C o m a n
LOCATION gal era Acres Sx^perfund Site 8L-4 Area
DATES INCLUDED IN SUMMARY
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09111995 1023 6172739084 CASHINS ASSOCIATES PAGE 01
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DATES INCLUDED IN SUMMARY
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Industrial Hygitnf amp CmimnmenUl Tinting
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
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LOCATION Salem Acres Superfund Site SL-4 Area
DATES INCLUDED IN SUMMARY
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WEEKLY HEALTH 6 SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Fortjl Cqjapany
LOCATION Salem Acrlaquoa Superfund Site 9L-4 Area
DATES INCLUDED IN SUMMARY
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Industrial Hygiene amp Emironmvntal Testing
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Company
LOCATION Salem Acres Superfund Site SL-4 Area
DATES INCLUDED IN SUMMARY J_
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Industrial Hygifnr amp [nvironmenljl res
SERIOUS HAZARD NOTIFICATION
ISSUED TO REPRESENTING
ISSUED BY REPRESENTING CASHINS S ASSOCIATES INcT DAY DATE ISSUED O04Xmdash 1 bull-bullmdashbull f P^JT
PROJECT NAME_ SITE LOCATION
THE PURPOSE OF THE FOLLOWING STATEMENT IS TO DOCUMENT THE EXISTENCE OF A CONDITION OR CONCERN WHICH CASHINS amp ASSOCIATES INC BELIEVES WARRANTS IMMEDIATE CORRECTIVE ACTION POSSIBLE SOLUTIONS AND OR CORRECTIVE ACTIONS WILL BE INCLUDED IN THIS NOTIFICATION WHEN POSSIBLE THIS NOTIFICATION IS LIMITED TO SITUATIONS THAT REPRESENT EITHER IMMEDIATE DANGER TO LIFE OR HEALTH CONDITIONS OR PREVIOUSLY IDENTIFIED CHRONIC PROBLEMS THAT UNDERMINE OUR ABILITY TO EFFECTIVELY INSURE COMPLIANCE WITH THE REQUIREMENTS OF THE HEALTH AND SAFETY PLAN
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Industrial Hygirne amp Cmimnmtntal Testing
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Company
LOCATION Salem Acres Superfund Site SL-4 Area
DATES INCLUDED IN SUMMARY T
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WEEKLY HEALTH amp SA7STT PLAN COMPLIANCE SUMMARY REPORT
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LOCATION Sa^am Acras Super fund 5 jte SL-4 Area
DATES INCLUDED IN SUMMARY bull
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07161996 1650 617944408 CASHING 3 ASSOCIATES PAGE 05
CASHINSamp Associates Inc
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CASHIMS amp ASSOCIATES PAGE 04 07161996 1658 6179444032
OVSHINSamp Associates Inc
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Company T
LOCATION Salem AcrM Suoerfund Stta 8L-4 Araa
DATES INCLUDED IN SUMMARY
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CASHINS amp Associates Inc
WBBKLY HEALTH amp SAFETY FLAK COMPLIANCE SUMMARY REPORT
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- barcode 14732
- barcodetext SEMS Doc ID 14732
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TARGET SHEET
THE MATERIAL DESCRIBED BELOW WAS NOT SCANNED BECAUSE
(X) OVERSIZED
() NON-PAPER MEDIA
() OTHER
DESCRIPTION DOC 14732 DRAFT FINAL REMEDIAL CONSTRUCTION REPORT FIGURE 3 TOPOGRAPHIC PLAN SL-4 AREA BOTTOM OF FLY ASH SALEM ACRES SHEET 1 OF 1
THE OMITTED MATERIAL IS AVAILABLE FOR REVIEW BY APPOINTMENT
AT THE EPA NEW ENGLAND SUPERFUND RECORDS CENTER BOSTON MA
TARGET SHEET
THE MATERIAL DESCRIBED BELOW WAS NOT SCANNED BECAUSE
(X) OVERSIZED
() NON-PAPER MEDIA
() OTHER
DESCRIPTION DOC 14732 DRAFT FINAL REMEDIAL CONSTRUCTION REPORT FIGURE 4 TOPOGRAPHIC PLAN SL-4 AREA LIMIT OF REMEDIATION SALEM ACRES SHEET 1OF1
THE OMITTED MATERIAL IS AVAILABLE FOR REVIEW BY APPOINTMENT
AT THE EPA NEW ENGLAND SUPERFUND RECORDS CENTER BOSTON MA
TARGET SHEET
THE MATERIAL DESCRIBED BELOW WAS NOT SCANNED BECAUSE
(X) OVERSIZED
() NON-PAPER MEDIA
() OTHER
DESCRIPTION DOC 14732 DRAFT FINAL REMEDIAL CONSTRUCTION REPORT FIGURE 5 TOPOGRAPHIC PLAN SL-4 AREA AS-BUILT PLAN SALEM ACRES SHEET 1 OF 1
THE OMITTED MATERIAL IS AVAILABLE FOR REVIEW BY APPOINTMENT
AT THE EPA NEW ENGLAND SUPERFUND RECORDS CENTER BOSTON MA
(i)
^mft^m
VIEW OF BARCELONA AVENUE THROUGH ENTRANCE GATE PRECONT RUCTION
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(2)
VIEW OF ACCESS ROAD LOOKING NORTH SL-4 ON LEFT PRECONSTRUCTION
VIEW OF ACCESS ROAD LOOKING NORTH SL-4 ON LEFT DA-1 TO LEFT OF PICKUP TRUCK
PRECONSTRUCTION
(3)
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
O ID a CO z O OHI
CO UJ
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(5)
VIEW OF BOUNDARY BETWEEN SL-4 AND DA-1 LOOKING WEST PRECONSTRUCTION
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(6)
EROSION CONTROLS LOOKING NORTH FROM CORNER OF SL-4SL-5 ADJACENT TO WA-1 PRECONSTRUCTION
(7)
TRUCK LOADING PAD LOOKING NORTHWEST FROM SUPPORT ZONE
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(8)
DECONTAMINATION PAD LOOKING NORTHWEST FROM SUPPORT ZONE
(9)
EXCAVATION OF FLY ASH LOOKING NORTHWEST FROM CRZ NOTE WATER FOR DUST CONTROL
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(10)
VIEW LOOKING WEST AFTER REMOVAL OF FLY ASH NOTE WA-1 BEYOND EROSION CONTROLS
(11)
EXCAVATION OF CONTAMINATED OVERBURDEN LOOKING SOUTH FROM DA-1 BOUNDARY
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(12)
VIEW OF RESTORED SITE LOOKING WEST TOWARD WA-1
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VIEW OF RESTORED SITE LOOKING NORTH TOWARD DA-1 ALONG ACCESS ROAD
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(15)
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VIEW OF RESTORED SITE ON DA-1 SJDE OF FENCE - LOOKING ST
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(18)
VIEW OF RESTORED SITE ON DA-1 SIDE OF FENCE - LOOKING WEST SL-4 ON RIGHT
APPENDIX A
ANALYTICAL RESULTS FOR
PONDED WATER
110795 1638 copy617 890 3883 TMA-WALTHAM ] 002007
PRELIMINARY REPORT UNAUDITED RESULTS
Thenno Analytical 300 Second Avenue PO Box 521 Waltham HA 02254
Attn Client Services Phone (617) 890-7200
Cashins amp Associates Order S5-11-034 55 Cambridge Street Date 110795 1522 Burlington HA 01803 Work ID Salem Acres Water
Date Received 110295 Attn Bob Cashins Date Completed
Purchase Order NA Invoice Number Client Code CASHINS
SAMPLE IDENTIFICATION
Sample Sample Number Description 01 11019S-924-01A
Sample Number 04
Sample Description
110195-9Z4-01D 02 110195-924-01B 05 110195-924-01E 03 110195-924-01C
Certified By
110795 1638 copy617 890 3883 TMA-WALTHAM 003007
PRELIMINARY REPORT UNAUDITED RESULTS
Order f S5-11-034 Thermo Analytical Page 2 110795 1522 TEST RESULTS BY SAHPLE
Test Description Volatile Organics- Aqueous Method EPA_8240 Test Code Collected 110195 02-00 Category WATER
DATE INJECTED 110695 DILUTION FACTOR 100 All results reported 1n ugL
COMPOUND RESULT DET LIMIT COMPOUND RESULT
Chloromethane U 10 Broroodi chl oromethane U Vinyl Chloride U 10 2-Chloroethyl Vinyl Ether U
Bromxnethane U 10 4-dethyl -2-pentanone U Chloroethane U 10 c1 3-1 3-Di chl oropropene U
Trichlorofluoronwthane U 50 Tol uene U Acetone 17 10 trans-1 3-Di chl oropropene LI
11-Oichloroethene U 50 11 2-Tri chl oroethane J Carbon Dlsulfide U 50 2-Hexanone U
Methyl ene Chloride U 50 Tetrachl oroethene U 12-Oichloroethene (total) U 50 D1 bromochl oromethane U
11-01 Chloroethane U 50 Chlorobenzene U Vinyl Acetate U 10 Ethyl benzene U
2-Butanone U 10 in and p-Xylene U Chloroform U 50 o-Xylene U
111-Tri Chloroethane U 50 Styrene U Carbon Tetrachlortde U 50 Broraoform U
Benzene U 50 112 2-Tat rachl oroethane U 12-01 Chloroethane U 50 1 3-01 chl orobenzene U
Trichloroethene U 50 I 4-Di chl orobenzene U 12-Dichloropropane U 50 12-01 chl orobenzene U
SURROGATE STANDARDS RESULT LEVEL X RECOVERY
12-Dichloroethane-D4 52 50 104 Toluene-08 47 50 94
l-Bromo-4-fluorobenzene 56 50 112
NOTES AND DEFINITIONS FOR THIS REPORT U =bull Undetected at stated detection limit
VOAJI
OET LIMIT
50 50
10 50 50 50 50 10
5 0 50 5 0 5 0 50 50 50 50 50 50 50 50
110795 1639 copy617 890 3883 TMA-WALTHAM copy004007
PRELIMINARY REPORT UNAUDITED RESULTS
Order t S5-11-034 Thermo Analytical Page 4 110795 1522 TEST RESULTS BY SAMPLE
ianple Description 110195-924-010 Lab No 04A Test Description RCRA Metals 1n Water Method SW846 Test Code
Collected 110195 0200 Category WATER
METAL RESULT DETECTION LIMIT METAL RESULT DETECTION LIMIT
Ag Silver U 10 As Arsenic 870 50
Ba Bar inn B69 10 Pb Lead U 50
Cd Cadmium U 50 Se Sel en1 um Z15 50
Cr Chromi um U 20 Hg Mercury U 020
NOTES AND DEFINITIONS FOR THIS REPORT All results reported in ugL U gt Undetected at stated detection limit
110795 1640 Q617 890 3883 TMA-WALTHAM 0005007
PRELIMINARY REPORT UNAUDITED RESULTS
Order S5-11-034 Thermo Analytical Page 5 110795 1522 REGULAR TEST RESULTS BY TEST
Chemical Oxygen Demand Mlnimun Maximum Method EPA600 4101
Sap Sample Description Result Units Limit Prepared Analyzed By 05A 110195-924-01E 64 bullgL 50 110395 110395 JD
Petroleum Hydrocarbons-H20 Minimum Maximum Method EPA600 4181
Samp Sample Description Result Units Limit Prepared Analyzed By 01A 110195-924-01A 108 mgL 050 110395 110395 JO
110795 1640 reg617 890 3883 TMA-WALTHAM copy006007
PRELIMINARY REPORT UNAUDITED RESULTS
Order I S5-11-034 Therm Analytical Page 6 110795 1522 TEST METHODOLOGIES
USEPA Test Methods for Evaluating Solid Wastes (SUS46 Third Edition) Method 7470 - Preparation of water for Mercury analysis
USEPA Test Methods for Evaluating Solid Vastes (SW846 Third Edition) Method 3010 - Add digestion of aqueous samples and extracts for total metals for analysis by Flame Atomic Absorption Spectroscopy or Inductively Coupled Plasma Spectroscopy
USEPA Test Methods for Evaluating Solid Vastes (SWB46 Third Edition Method 8270 mdash Gas ChroroatographyMass Spectrometry for PAHs
Volatile Organics in Water - Hazardous Substance List
SV846 Method 8240 - Modified
Test Methods for Evaluating Solid Waste SU-846 US EPA Office of Solid Waste and Emergency Response Washington 3rd Edition
Aqueous sanples are analyzed in accordance with Method 8240 using a purge and trap technique followed by 64s ChromatographyMass Spectroscopy
Quality assurance procedures for GCMS Include daily tuning and calibration of the mass spectrometer and the use of surrogate standards in each sample to monitor method performance Quantitatton is performed by the Internal standard method Analysis of blanks duplicate samples and standards are run frequently as further quality assurance procedures
USEPA Test Methods for Evaluating Solid Wastes (SW846 Third Edition) Method 3S10 mdash Separatory Funnel Liquid-Liquid Extraction
EPA-6004-79-020 - Chemical Oxygen Demand - Titrimetric Mid-Level Method 4101
EPA6004-79-020 - Petroleum Hydrocarbons 1n Water Total Recoverable Method 4181 (Spectrophotometric Infrared)
110795 1641 copy617 890 3883 TMA-WALTHAM copy007007
APPENDIX B
QUANTITY SURVEY DOCUMENTATION
TFMORAN INC Surveying - Engineering - Land Planning SoilsWetlands Mapping - Landscape Architecture
January 15 1996
Mr Jack Enos Vice President TFord Company Inc 118 Tenney Street Georgetown MA 01833
RE Survey Results - Salem Acres - SL4 Area Salem Massachusetts
Dear Jack
This letter amends the letter of December 13 1995 per our review last week
TFMoran Inc performed topographic surveys at the Salem Acres site on April 21 1994 for GEI Consultants prior to removal of material and for TFord Company on October 18 1995 after the removal of material The survey data from the original survey in 1994 was adjusted thirty feet higher to correct for a datum difference from current site datum This was due to the original reporting of the Site Benchmark (TP34) elevation as 11464 rather than 14464 which is the correct elevation
Once both topographic surfaces were on the site datum the raw cut volume was obtained by Eaglepoint (Volumes Module) Software utilizing the prismoidal method comparing the two surfaces For reference please see the attached topographic plan which superimposes the October 15 1995 contours (dark lines) over the April 21 1994 contours The volume is based on the intersection of the two surfaces Also it was noted that stock piles of material did exist on site which were not surveyed at the time
The final raw cut volume arrived at by the above methods is 12749 Cubic Yards
In November and December of 1995 the site was resurveyed to locate the area of exposed ledge at the site The results of this survey are shown on the attached topographic worksheet dated November 3 1995 and last revised January 15 1996 The results of the survey indicate the total site area to be 50860 sq ft or 117 acres The total area of exposed ledge surveyed is 19990 sq ft or 46 acres If you have any questions regarding the above call me directly Thank you
Sincerely
John W Myhaver Jr ^_ Field Operations Manager
Enclosure ItorLltr
Route 101 Bedford NH 03110 Phone (603) 472-4488 FAX (603) 472-9747
APPENDIX C
HEALTH AND SAFETY PHASE-OUT REPORT
HEALTH AND SAFETY PHASE-OUT REPORT SALEM ACRES SL-4 AREA
Introduction
During remediation work on SL-4 Health and Safety Monitoring was performed Cashins amp Associates Inc of Reading MA performed the following work as a subcontractor to TFCI
1) Preparation of a site-specific Health and Safety Plan (dated September 1 1995)
2) Provide a Field TechnicianIndustrial Hygienist to serve as Site Safety and Health Officer (SSHO) and to conduct air and noise monitoring
3) Provide a Certified Industrial Hygienist to review Health and Safety and to conduct site specific training (record of training included at end of Appendix C)
4) Collect 8-hour air samples for worker exposure and ambient air at the Barcelona Avenue gate Arrange for analysis of the samples and report results
5) Prepare daily and weekly Health and Safety reports
6) Prepare a Health and Safety Phase-Out Report
In general the following health and safety practices were followed
1) All workers wore hard hats safety glasses work boots gloves and hearing protection as minimum level PPE
2) When working in the exclusion zone workers wore in addition to above tyvek rubber overboots and rubber coated gloves When dust was a potential concern an industrial grade dustmist mask was also worn This level of PPE was considered Level D modified
3) Workers leaving the exclusion zone removed PPE (tyveks gloves boots and masks) in the support zone and either disposed of the items or decontaminated them
4) Workers andor visitors without 40-hour OSHA training were not permitted to enter the exclusion zone
Attached is a report prepared by Cashins amp Associates along with weekly Health and Safety Summary Reports prepared by the Field Hygienist In summary the air monitoring results indicate no levels exceeding the applicable exposure guidelines except one instance
During excavation of contaminated overburden in the northwest comer of the site an area of VOC contaminated soil was encountered Total VOCs levels measured using a PID exceeded the action level established in the Health and Safety Plan The SSHO advised TFCI to upgrade to Level C PPE in order to backfill the excavation in this area TFCI equipment operator upgraded and backfilled the area The SSHO in consultation with the Cashins CIH advised TFCI to avoid work in this area until the contaminants were characterized GEI sampled the material for waste characterization analysis and provided the results to TFCI Based on the results an action level was established by the CIH for the specific contaminants found Further PID measurements indicated levels below the new action level and work was resumed
The noise monitoring indicated that the noise level at the Barcelona Avenue gate was not exceeded Only one instance of excess noise level in the work zone was recorded (10 db(a) above the ambient noise level or 85 db(a)) Workers wore hearing protection in this instance
mdash 07171996 1601 6179444032 CASHIMS S ASSOCIATES PAGE 02
CASHINS amp Associates Inc
ItxhalrM Hy-gifnr A Invtronmtnltl Tttling
July 17 1996
Mr Jack Enos T Ford Company Inc USTenney Street Georgetown MA 01833
Dear Jack
The Site Safety and Health Officer (SSHO) from Cashing amp Associates Inc performed daily inspections of the SL-4 area Salem Acres Superfund Site between 9595 and 12195 in accordance with the Health amp Safety Plan (HSP) for the site Daily inspection logs were submitted every day No accidentsincidents were reported during the work period
In accordance with the Health amp Safety Plan the SSHO performed daily air and noise monitoring at the site during Ac project Samples were collected for metals (lead beryllium chromium arsenic) and Polynuclear Aromatic Hydrocarbons (PAHs) at the site perimeter and for workers exposure determination Coal Tar Pitch Volatiles (a benzene soluble extractables) were also used to determine the workers exposure to PAH compounds Coal Tar Pitch Volatiles (CTPV) were analyzed using OSHA 58 Method If CTPV levels oq personal samples exceed the site criteria of 02 ragm3 the sample was submitted for PAHs analysis All air samples on the site perimeter were analyzed for PAH compounds
Site monitoring air sample collection and results report were done under the supervision of a Certified Industrial Hygienist
Full shift personal worker exposure samples were collected once a week Ambient air samples were collected at the Barcelona Avenue gate about 20 feet to the west of the site gate to determine if site contaminants were migrating off site The ambient air samples were also collected once a week during the project except on rainy days and days without work with contaminated soil
All air samples were analyzed by the American Industrial Hygiene Association accredited ESA Laboratories Inc using the following methods PAHs - NIOSH 5515 Lead - NIOSH 7082 Beryllium - NIOSH 7102 Chromium - NIOSH 7024 Arsenic - NIOSH 7900 Coal Tar Pitch Volatiles - OSHA 58 All methods used are accepted by the industrial hygiene community for 8-hour exposure assessment EPA methods are usually used for ambient air measurements
CRErORTTFOmiOO
80 Mam Street bull Reading MA 01867 bull Phone- 61 7-944-4060 bull Fax 61 7-944-4082
07171996 1601 6179444032 CASHIMS amp ASSOCIATES PAGE 03
The results of air samples for metals and PAHs are presented in Table No 1
All concentrations of metals and PAHs at the site perimeter (Barcelona Avenue) and active work zones were below the OSHA Permissible Exposure Limits (PEL) and the American Conference of Governmental Industrial Hygicnists Threshold Limit Value (ACGIH TLV) Two personal samples collected on October 19 and October 23rd showed Coal Tar Pitch Volatiles (CTPV) results above OSHA PEL and AIHA TLV limits Both samples were resubmittcd to the lab for further analysis to determine if PAH compounds are present because the CTPV results were above site criteria
The results of the PAH concentrations for the personal sample on Mark Goodwin on October 19 1995 during excavation and washing trucks and for the personal sample on Ron Maker on October 23 1995 during excavating and cleaning rocks by compressed air were below OSHA PEL and ACGIH TLV limits
The SSHO performed noise monitoring according to the HSP at the exclusion zone and at the Barcelona Avenue site perimeter fence A Dupont sound level meter was used for noise monitoring The noise level in the exclusion zone during all operations except one did not exceed the on site criteria of 85 dB(a) During a short time when the air compressor had been used to clean rocks the sound level in the exclusion zone next to the air compressor did exceed 85 dB(a) Ear protection devices were worn by the workers during that operation At no time did the noise level at the Barcelona Avenue site perimeter exceed 10 dB(a) above the ambient noise level or 85 dB(a)
The SSHO performed total dust monitoring on a daily basis during the project at the site perimeter downwind of work location and at the site gate using a Miniram real time dust meter The summary of dust monitoring is presented in Table No 2 Total dust concentrations on site and off site did not exceed site criteria of 1 mgm3 and the action level of 05 nigny1
The summary of air monitoring for Volatile Organic Compounds (VOC) is presented in Table No 3 VOC concentrations in the working area did not exceed the on site criteria of 5 ppm in a breathing zone VOC concentrations on the site perimeter did not exceed real time off site criteria of 2 ppm
Five detail reports with results of air sampling were submitted during the project period
Sincerely Cashins amp Associates Inc
Evelina Vaughan Industrial Hygieflfst
CASHINS amp ASSOCIATES Inc
80 Mam Street bull Reading MA 01867 bull Phone61 7-944-4060 bull Fax 617-944-4082
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WEEKLY HEALTH 6 SAFETY PLAN COMPLIANCE SUMMARY REPORT
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CLIENT T Ford Company
LOCATION Salem Acres Superfund Site SL-4 Area
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ISSUED BY REPRESENTING CASHINS S ASSOCIATES INcT DAY DATE ISSUED O04Xmdash 1 bull-bullmdashbull f P^JT
PROJECT NAME_ SITE LOCATION
THE PURPOSE OF THE FOLLOWING STATEMENT IS TO DOCUMENT THE EXISTENCE OF A CONDITION OR CONCERN WHICH CASHINS amp ASSOCIATES INC BELIEVES WARRANTS IMMEDIATE CORRECTIVE ACTION POSSIBLE SOLUTIONS AND OR CORRECTIVE ACTIONS WILL BE INCLUDED IN THIS NOTIFICATION WHEN POSSIBLE THIS NOTIFICATION IS LIMITED TO SITUATIONS THAT REPRESENT EITHER IMMEDIATE DANGER TO LIFE OR HEALTH CONDITIONS OR PREVIOUSLY IDENTIFIED CHRONIC PROBLEMS THAT UNDERMINE OUR ABILITY TO EFFECTIVELY INSURE COMPLIANCE WITH THE REQUIREMENTS OF THE HEALTH AND SAFETY PLAN
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LOCATION Salem Acres Superfund Site SL-4 Area
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07161996 1650 617944408 CASHING 3 ASSOCIATES PAGE 05
CASHINSamp Associates Inc
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CASHIMS amp ASSOCIATES PAGE 04 07161996 1658 6179444032
OVSHINSamp Associates Inc
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CLIENT T Ford Company T
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07151996 18 fO 6179444082 CASHINS S ASSOCIATES PAGE 02
CASHINS amp Associates Inc
WBBKLY HEALTH amp SAFETY FLAK COMPLIANCE SUMMARY REPORT
CLIENT T Ford Compapv
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- barcode 14732
- barcodetext SEMS Doc ID 14732
![Page 17: SALEM ACRES SUPERFUND SITE SALEM, MA ...The truck loading pa d consisted of a crushed stone are sea t up along the east sid e o f SL-4 adjacent to the access road A. row of concrete](https://reader036.vdocuments.us/reader036/viewer/2022070114/60729b840fec4e6b4d136a16/html5/thumbnails/17.jpg)
TARGET SHEET
THE MATERIAL DESCRIBED BELOW WAS NOT SCANNED BECAUSE
(X) OVERSIZED
() NON-PAPER MEDIA
() OTHER
DESCRIPTION DOC 14732 DRAFT FINAL REMEDIAL CONSTRUCTION REPORT FIGURE 4 TOPOGRAPHIC PLAN SL-4 AREA LIMIT OF REMEDIATION SALEM ACRES SHEET 1OF1
THE OMITTED MATERIAL IS AVAILABLE FOR REVIEW BY APPOINTMENT
AT THE EPA NEW ENGLAND SUPERFUND RECORDS CENTER BOSTON MA
TARGET SHEET
THE MATERIAL DESCRIBED BELOW WAS NOT SCANNED BECAUSE
(X) OVERSIZED
() NON-PAPER MEDIA
() OTHER
DESCRIPTION DOC 14732 DRAFT FINAL REMEDIAL CONSTRUCTION REPORT FIGURE 5 TOPOGRAPHIC PLAN SL-4 AREA AS-BUILT PLAN SALEM ACRES SHEET 1 OF 1
THE OMITTED MATERIAL IS AVAILABLE FOR REVIEW BY APPOINTMENT
AT THE EPA NEW ENGLAND SUPERFUND RECORDS CENTER BOSTON MA
(i)
^mft^m
VIEW OF BARCELONA AVENUE THROUGH ENTRANCE GATE PRECONT RUCTION
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(2)
VIEW OF ACCESS ROAD LOOKING NORTH SL-4 ON LEFT PRECONSTRUCTION
VIEW OF ACCESS ROAD LOOKING NORTH SL-4 ON LEFT DA-1 TO LEFT OF PICKUP TRUCK
PRECONSTRUCTION
(3)
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
O ID a CO z O OHI
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VIEW OF BOUNDARY BETWEEN SL-4 AND DA-1 LOOKING WEST PRECONSTRUCTION
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(6)
EROSION CONTROLS LOOKING NORTH FROM CORNER OF SL-4SL-5 ADJACENT TO WA-1 PRECONSTRUCTION
(7)
TRUCK LOADING PAD LOOKING NORTHWEST FROM SUPPORT ZONE
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(8)
DECONTAMINATION PAD LOOKING NORTHWEST FROM SUPPORT ZONE
(9)
EXCAVATION OF FLY ASH LOOKING NORTHWEST FROM CRZ NOTE WATER FOR DUST CONTROL
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(10)
VIEW LOOKING WEST AFTER REMOVAL OF FLY ASH NOTE WA-1 BEYOND EROSION CONTROLS
(11)
EXCAVATION OF CONTAMINATED OVERBURDEN LOOKING SOUTH FROM DA-1 BOUNDARY
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(12)
VIEW OF RESTORED SITE LOOKING WEST TOWARD WA-1
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VIEW OF RESTORED SITE LOOKING NORTH TOWARD DA-1 ALONG ACCESS ROAD
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(15)
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ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(18)
VIEW OF RESTORED SITE ON DA-1 SIDE OF FENCE - LOOKING WEST SL-4 ON RIGHT
APPENDIX A
ANALYTICAL RESULTS FOR
PONDED WATER
110795 1638 copy617 890 3883 TMA-WALTHAM ] 002007
PRELIMINARY REPORT UNAUDITED RESULTS
Thenno Analytical 300 Second Avenue PO Box 521 Waltham HA 02254
Attn Client Services Phone (617) 890-7200
Cashins amp Associates Order S5-11-034 55 Cambridge Street Date 110795 1522 Burlington HA 01803 Work ID Salem Acres Water
Date Received 110295 Attn Bob Cashins Date Completed
Purchase Order NA Invoice Number Client Code CASHINS
SAMPLE IDENTIFICATION
Sample Sample Number Description 01 11019S-924-01A
Sample Number 04
Sample Description
110195-9Z4-01D 02 110195-924-01B 05 110195-924-01E 03 110195-924-01C
Certified By
110795 1638 copy617 890 3883 TMA-WALTHAM 003007
PRELIMINARY REPORT UNAUDITED RESULTS
Order f S5-11-034 Thermo Analytical Page 2 110795 1522 TEST RESULTS BY SAHPLE
Test Description Volatile Organics- Aqueous Method EPA_8240 Test Code Collected 110195 02-00 Category WATER
DATE INJECTED 110695 DILUTION FACTOR 100 All results reported 1n ugL
COMPOUND RESULT DET LIMIT COMPOUND RESULT
Chloromethane U 10 Broroodi chl oromethane U Vinyl Chloride U 10 2-Chloroethyl Vinyl Ether U
Bromxnethane U 10 4-dethyl -2-pentanone U Chloroethane U 10 c1 3-1 3-Di chl oropropene U
Trichlorofluoronwthane U 50 Tol uene U Acetone 17 10 trans-1 3-Di chl oropropene LI
11-Oichloroethene U 50 11 2-Tri chl oroethane J Carbon Dlsulfide U 50 2-Hexanone U
Methyl ene Chloride U 50 Tetrachl oroethene U 12-Oichloroethene (total) U 50 D1 bromochl oromethane U
11-01 Chloroethane U 50 Chlorobenzene U Vinyl Acetate U 10 Ethyl benzene U
2-Butanone U 10 in and p-Xylene U Chloroform U 50 o-Xylene U
111-Tri Chloroethane U 50 Styrene U Carbon Tetrachlortde U 50 Broraoform U
Benzene U 50 112 2-Tat rachl oroethane U 12-01 Chloroethane U 50 1 3-01 chl orobenzene U
Trichloroethene U 50 I 4-Di chl orobenzene U 12-Dichloropropane U 50 12-01 chl orobenzene U
SURROGATE STANDARDS RESULT LEVEL X RECOVERY
12-Dichloroethane-D4 52 50 104 Toluene-08 47 50 94
l-Bromo-4-fluorobenzene 56 50 112
NOTES AND DEFINITIONS FOR THIS REPORT U =bull Undetected at stated detection limit
VOAJI
OET LIMIT
50 50
10 50 50 50 50 10
5 0 50 5 0 5 0 50 50 50 50 50 50 50 50
110795 1639 copy617 890 3883 TMA-WALTHAM copy004007
PRELIMINARY REPORT UNAUDITED RESULTS
Order t S5-11-034 Thermo Analytical Page 4 110795 1522 TEST RESULTS BY SAMPLE
ianple Description 110195-924-010 Lab No 04A Test Description RCRA Metals 1n Water Method SW846 Test Code
Collected 110195 0200 Category WATER
METAL RESULT DETECTION LIMIT METAL RESULT DETECTION LIMIT
Ag Silver U 10 As Arsenic 870 50
Ba Bar inn B69 10 Pb Lead U 50
Cd Cadmium U 50 Se Sel en1 um Z15 50
Cr Chromi um U 20 Hg Mercury U 020
NOTES AND DEFINITIONS FOR THIS REPORT All results reported in ugL U gt Undetected at stated detection limit
110795 1640 Q617 890 3883 TMA-WALTHAM 0005007
PRELIMINARY REPORT UNAUDITED RESULTS
Order S5-11-034 Thermo Analytical Page 5 110795 1522 REGULAR TEST RESULTS BY TEST
Chemical Oxygen Demand Mlnimun Maximum Method EPA600 4101
Sap Sample Description Result Units Limit Prepared Analyzed By 05A 110195-924-01E 64 bullgL 50 110395 110395 JD
Petroleum Hydrocarbons-H20 Minimum Maximum Method EPA600 4181
Samp Sample Description Result Units Limit Prepared Analyzed By 01A 110195-924-01A 108 mgL 050 110395 110395 JO
110795 1640 reg617 890 3883 TMA-WALTHAM copy006007
PRELIMINARY REPORT UNAUDITED RESULTS
Order I S5-11-034 Therm Analytical Page 6 110795 1522 TEST METHODOLOGIES
USEPA Test Methods for Evaluating Solid Wastes (SUS46 Third Edition) Method 7470 - Preparation of water for Mercury analysis
USEPA Test Methods for Evaluating Solid Vastes (SW846 Third Edition) Method 3010 - Add digestion of aqueous samples and extracts for total metals for analysis by Flame Atomic Absorption Spectroscopy or Inductively Coupled Plasma Spectroscopy
USEPA Test Methods for Evaluating Solid Vastes (SWB46 Third Edition Method 8270 mdash Gas ChroroatographyMass Spectrometry for PAHs
Volatile Organics in Water - Hazardous Substance List
SV846 Method 8240 - Modified
Test Methods for Evaluating Solid Waste SU-846 US EPA Office of Solid Waste and Emergency Response Washington 3rd Edition
Aqueous sanples are analyzed in accordance with Method 8240 using a purge and trap technique followed by 64s ChromatographyMass Spectroscopy
Quality assurance procedures for GCMS Include daily tuning and calibration of the mass spectrometer and the use of surrogate standards in each sample to monitor method performance Quantitatton is performed by the Internal standard method Analysis of blanks duplicate samples and standards are run frequently as further quality assurance procedures
USEPA Test Methods for Evaluating Solid Wastes (SW846 Third Edition) Method 3S10 mdash Separatory Funnel Liquid-Liquid Extraction
EPA-6004-79-020 - Chemical Oxygen Demand - Titrimetric Mid-Level Method 4101
EPA6004-79-020 - Petroleum Hydrocarbons 1n Water Total Recoverable Method 4181 (Spectrophotometric Infrared)
110795 1641 copy617 890 3883 TMA-WALTHAM copy007007
APPENDIX B
QUANTITY SURVEY DOCUMENTATION
TFMORAN INC Surveying - Engineering - Land Planning SoilsWetlands Mapping - Landscape Architecture
January 15 1996
Mr Jack Enos Vice President TFord Company Inc 118 Tenney Street Georgetown MA 01833
RE Survey Results - Salem Acres - SL4 Area Salem Massachusetts
Dear Jack
This letter amends the letter of December 13 1995 per our review last week
TFMoran Inc performed topographic surveys at the Salem Acres site on April 21 1994 for GEI Consultants prior to removal of material and for TFord Company on October 18 1995 after the removal of material The survey data from the original survey in 1994 was adjusted thirty feet higher to correct for a datum difference from current site datum This was due to the original reporting of the Site Benchmark (TP34) elevation as 11464 rather than 14464 which is the correct elevation
Once both topographic surfaces were on the site datum the raw cut volume was obtained by Eaglepoint (Volumes Module) Software utilizing the prismoidal method comparing the two surfaces For reference please see the attached topographic plan which superimposes the October 15 1995 contours (dark lines) over the April 21 1994 contours The volume is based on the intersection of the two surfaces Also it was noted that stock piles of material did exist on site which were not surveyed at the time
The final raw cut volume arrived at by the above methods is 12749 Cubic Yards
In November and December of 1995 the site was resurveyed to locate the area of exposed ledge at the site The results of this survey are shown on the attached topographic worksheet dated November 3 1995 and last revised January 15 1996 The results of the survey indicate the total site area to be 50860 sq ft or 117 acres The total area of exposed ledge surveyed is 19990 sq ft or 46 acres If you have any questions regarding the above call me directly Thank you
Sincerely
John W Myhaver Jr ^_ Field Operations Manager
Enclosure ItorLltr
Route 101 Bedford NH 03110 Phone (603) 472-4488 FAX (603) 472-9747
APPENDIX C
HEALTH AND SAFETY PHASE-OUT REPORT
HEALTH AND SAFETY PHASE-OUT REPORT SALEM ACRES SL-4 AREA
Introduction
During remediation work on SL-4 Health and Safety Monitoring was performed Cashins amp Associates Inc of Reading MA performed the following work as a subcontractor to TFCI
1) Preparation of a site-specific Health and Safety Plan (dated September 1 1995)
2) Provide a Field TechnicianIndustrial Hygienist to serve as Site Safety and Health Officer (SSHO) and to conduct air and noise monitoring
3) Provide a Certified Industrial Hygienist to review Health and Safety and to conduct site specific training (record of training included at end of Appendix C)
4) Collect 8-hour air samples for worker exposure and ambient air at the Barcelona Avenue gate Arrange for analysis of the samples and report results
5) Prepare daily and weekly Health and Safety reports
6) Prepare a Health and Safety Phase-Out Report
In general the following health and safety practices were followed
1) All workers wore hard hats safety glasses work boots gloves and hearing protection as minimum level PPE
2) When working in the exclusion zone workers wore in addition to above tyvek rubber overboots and rubber coated gloves When dust was a potential concern an industrial grade dustmist mask was also worn This level of PPE was considered Level D modified
3) Workers leaving the exclusion zone removed PPE (tyveks gloves boots and masks) in the support zone and either disposed of the items or decontaminated them
4) Workers andor visitors without 40-hour OSHA training were not permitted to enter the exclusion zone
Attached is a report prepared by Cashins amp Associates along with weekly Health and Safety Summary Reports prepared by the Field Hygienist In summary the air monitoring results indicate no levels exceeding the applicable exposure guidelines except one instance
During excavation of contaminated overburden in the northwest comer of the site an area of VOC contaminated soil was encountered Total VOCs levels measured using a PID exceeded the action level established in the Health and Safety Plan The SSHO advised TFCI to upgrade to Level C PPE in order to backfill the excavation in this area TFCI equipment operator upgraded and backfilled the area The SSHO in consultation with the Cashins CIH advised TFCI to avoid work in this area until the contaminants were characterized GEI sampled the material for waste characterization analysis and provided the results to TFCI Based on the results an action level was established by the CIH for the specific contaminants found Further PID measurements indicated levels below the new action level and work was resumed
The noise monitoring indicated that the noise level at the Barcelona Avenue gate was not exceeded Only one instance of excess noise level in the work zone was recorded (10 db(a) above the ambient noise level or 85 db(a)) Workers wore hearing protection in this instance
mdash 07171996 1601 6179444032 CASHIMS S ASSOCIATES PAGE 02
CASHINS amp Associates Inc
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July 17 1996
Mr Jack Enos T Ford Company Inc USTenney Street Georgetown MA 01833
Dear Jack
The Site Safety and Health Officer (SSHO) from Cashing amp Associates Inc performed daily inspections of the SL-4 area Salem Acres Superfund Site between 9595 and 12195 in accordance with the Health amp Safety Plan (HSP) for the site Daily inspection logs were submitted every day No accidentsincidents were reported during the work period
In accordance with the Health amp Safety Plan the SSHO performed daily air and noise monitoring at the site during Ac project Samples were collected for metals (lead beryllium chromium arsenic) and Polynuclear Aromatic Hydrocarbons (PAHs) at the site perimeter and for workers exposure determination Coal Tar Pitch Volatiles (a benzene soluble extractables) were also used to determine the workers exposure to PAH compounds Coal Tar Pitch Volatiles (CTPV) were analyzed using OSHA 58 Method If CTPV levels oq personal samples exceed the site criteria of 02 ragm3 the sample was submitted for PAHs analysis All air samples on the site perimeter were analyzed for PAH compounds
Site monitoring air sample collection and results report were done under the supervision of a Certified Industrial Hygienist
Full shift personal worker exposure samples were collected once a week Ambient air samples were collected at the Barcelona Avenue gate about 20 feet to the west of the site gate to determine if site contaminants were migrating off site The ambient air samples were also collected once a week during the project except on rainy days and days without work with contaminated soil
All air samples were analyzed by the American Industrial Hygiene Association accredited ESA Laboratories Inc using the following methods PAHs - NIOSH 5515 Lead - NIOSH 7082 Beryllium - NIOSH 7102 Chromium - NIOSH 7024 Arsenic - NIOSH 7900 Coal Tar Pitch Volatiles - OSHA 58 All methods used are accepted by the industrial hygiene community for 8-hour exposure assessment EPA methods are usually used for ambient air measurements
CRErORTTFOmiOO
80 Mam Street bull Reading MA 01867 bull Phone- 61 7-944-4060 bull Fax 61 7-944-4082
07171996 1601 6179444032 CASHIMS amp ASSOCIATES PAGE 03
The results of air samples for metals and PAHs are presented in Table No 1
All concentrations of metals and PAHs at the site perimeter (Barcelona Avenue) and active work zones were below the OSHA Permissible Exposure Limits (PEL) and the American Conference of Governmental Industrial Hygicnists Threshold Limit Value (ACGIH TLV) Two personal samples collected on October 19 and October 23rd showed Coal Tar Pitch Volatiles (CTPV) results above OSHA PEL and AIHA TLV limits Both samples were resubmittcd to the lab for further analysis to determine if PAH compounds are present because the CTPV results were above site criteria
The results of the PAH concentrations for the personal sample on Mark Goodwin on October 19 1995 during excavation and washing trucks and for the personal sample on Ron Maker on October 23 1995 during excavating and cleaning rocks by compressed air were below OSHA PEL and ACGIH TLV limits
The SSHO performed noise monitoring according to the HSP at the exclusion zone and at the Barcelona Avenue site perimeter fence A Dupont sound level meter was used for noise monitoring The noise level in the exclusion zone during all operations except one did not exceed the on site criteria of 85 dB(a) During a short time when the air compressor had been used to clean rocks the sound level in the exclusion zone next to the air compressor did exceed 85 dB(a) Ear protection devices were worn by the workers during that operation At no time did the noise level at the Barcelona Avenue site perimeter exceed 10 dB(a) above the ambient noise level or 85 dB(a)
The SSHO performed total dust monitoring on a daily basis during the project at the site perimeter downwind of work location and at the site gate using a Miniram real time dust meter The summary of dust monitoring is presented in Table No 2 Total dust concentrations on site and off site did not exceed site criteria of 1 mgm3 and the action level of 05 nigny1
The summary of air monitoring for Volatile Organic Compounds (VOC) is presented in Table No 3 VOC concentrations in the working area did not exceed the on site criteria of 5 ppm in a breathing zone VOC concentrations on the site perimeter did not exceed real time off site criteria of 2 ppm
Five detail reports with results of air sampling were submitted during the project period
Sincerely Cashins amp Associates Inc
Evelina Vaughan Industrial Hygieflfst
CASHINS amp ASSOCIATES Inc
80 Mam Street bull Reading MA 01867 bull Phone61 7-944-4060 bull Fax 617-944-4082
07171996 1601 6179444082 CASHINS S ASSOCIATES PAGE 04
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CASHINS amp Associates inc
Ifxtuitral Hygltne A fnvironmtnltt Tuning
W3SXLY HBALTH amp SAFETY PLAN COMPLIANCE SUMMARY R3PORT
CLIENT T foyd C o m a n
LOCATION gal era Acres Sx^perfund Site 8L-4 Area
DATES INCLUDED IN SUMMARY
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SUMMARIZED BY FOR CASHINS amp ASSOCIATES INC
55 CAMBRIDGE STREET bull SUITE 201 bull BURLINGTON MA 01803 laquo TEL 61 -273-9080 bull FAX 67-273-9C84
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WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Fprd Company
LOCATION Salen Acres Suoerfund Site SL-4 Area
DATES INCLUDED IN SUMMARY
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Industrial Hygitnf amp CmimnmenUl Tinting
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Compan
LOCATION Salem Acres Superfund Site SL-4 Area
DATES INCLUDED IN SUMMARY
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WEEKLY HEALTH 6 SAFETY PLAN COMPLIANCE SUMMARY REPORT
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LOCATION Salem Acrlaquoa Superfund Site 9L-4 Area
DATES INCLUDED IN SUMMARY
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Industrial Hygiene amp Emironmvntal Testing
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Company
LOCATION Salem Acres Superfund Site SL-4 Area
DATES INCLUDED IN SUMMARY J_
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THE PURPOSE OF THE FOLLOWING STATEMENT IS TO DOCUMENT THE EXISTENCE OF A CONDITION OR CONCERN WHICH CASHINS amp ASSOCIATES INC BELIEVES WARRANTS IMMEDIATE CORRECTIVE ACTION POSSIBLE SOLUTIONS AND OR CORRECTIVE ACTIONS WILL BE INCLUDED IN THIS NOTIFICATION WHEN POSSIBLE THIS NOTIFICATION IS LIMITED TO SITUATIONS THAT REPRESENT EITHER IMMEDIATE DANGER TO LIFE OR HEALTH CONDITIONS OR PREVIOUSLY IDENTIFIED CHRONIC PROBLEMS THAT UNDERMINE OUR ABILITY TO EFFECTIVELY INSURE COMPLIANCE WITH THE REQUIREMENTS OF THE HEALTH AND SAFETY PLAN
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WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
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LOCATION Salem Acres Superfund Site SL-4 Area
DATES INCLUDED IN SUMMARY T
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WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
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LOCATION Salem AcrM Suoerfund Stta 8L-4 Araa
DATES INCLUDED IN SUMMARY
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07151996 18 fO 6179444082 CASHINS S ASSOCIATES PAGE 02
CASHINS amp Associates Inc
WBBKLY HEALTH amp SAFETY FLAK COMPLIANCE SUMMARY REPORT
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LOCATION i Sal am Acrlaquolaquo Suparfund Sita SL-4 Area
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- barcode 14732
- barcodetext SEMS Doc ID 14732
![Page 18: SALEM ACRES SUPERFUND SITE SALEM, MA ...The truck loading pa d consisted of a crushed stone are sea t up along the east sid e o f SL-4 adjacent to the access road A. row of concrete](https://reader036.vdocuments.us/reader036/viewer/2022070114/60729b840fec4e6b4d136a16/html5/thumbnails/18.jpg)
TARGET SHEET
THE MATERIAL DESCRIBED BELOW WAS NOT SCANNED BECAUSE
(X) OVERSIZED
() NON-PAPER MEDIA
() OTHER
DESCRIPTION DOC 14732 DRAFT FINAL REMEDIAL CONSTRUCTION REPORT FIGURE 5 TOPOGRAPHIC PLAN SL-4 AREA AS-BUILT PLAN SALEM ACRES SHEET 1 OF 1
THE OMITTED MATERIAL IS AVAILABLE FOR REVIEW BY APPOINTMENT
AT THE EPA NEW ENGLAND SUPERFUND RECORDS CENTER BOSTON MA
(i)
^mft^m
VIEW OF BARCELONA AVENUE THROUGH ENTRANCE GATE PRECONT RUCTION
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(2)
VIEW OF ACCESS ROAD LOOKING NORTH SL-4 ON LEFT PRECONSTRUCTION
VIEW OF ACCESS ROAD LOOKING NORTH SL-4 ON LEFT DA-1 TO LEFT OF PICKUP TRUCK
PRECONSTRUCTION
(3)
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
O ID a CO z O OHI
CO UJ
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(5)
VIEW OF BOUNDARY BETWEEN SL-4 AND DA-1 LOOKING WEST PRECONSTRUCTION
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(6)
EROSION CONTROLS LOOKING NORTH FROM CORNER OF SL-4SL-5 ADJACENT TO WA-1 PRECONSTRUCTION
(7)
TRUCK LOADING PAD LOOKING NORTHWEST FROM SUPPORT ZONE
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(8)
DECONTAMINATION PAD LOOKING NORTHWEST FROM SUPPORT ZONE
(9)
EXCAVATION OF FLY ASH LOOKING NORTHWEST FROM CRZ NOTE WATER FOR DUST CONTROL
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(10)
VIEW LOOKING WEST AFTER REMOVAL OF FLY ASH NOTE WA-1 BEYOND EROSION CONTROLS
(11)
EXCAVATION OF CONTAMINATED OVERBURDEN LOOKING SOUTH FROM DA-1 BOUNDARY
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(12)
VIEW OF RESTORED SITE LOOKING WEST TOWARD WA-1
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VIEW OF RESTORED SITE LOOKING NORTH TOWARD DA-1 ALONG ACCESS ROAD
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(15)
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VIEW OF RESTORED SITE ON DA-1 SJDE OF FENCE - LOOKING ST
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(18)
VIEW OF RESTORED SITE ON DA-1 SIDE OF FENCE - LOOKING WEST SL-4 ON RIGHT
APPENDIX A
ANALYTICAL RESULTS FOR
PONDED WATER
110795 1638 copy617 890 3883 TMA-WALTHAM ] 002007
PRELIMINARY REPORT UNAUDITED RESULTS
Thenno Analytical 300 Second Avenue PO Box 521 Waltham HA 02254
Attn Client Services Phone (617) 890-7200
Cashins amp Associates Order S5-11-034 55 Cambridge Street Date 110795 1522 Burlington HA 01803 Work ID Salem Acres Water
Date Received 110295 Attn Bob Cashins Date Completed
Purchase Order NA Invoice Number Client Code CASHINS
SAMPLE IDENTIFICATION
Sample Sample Number Description 01 11019S-924-01A
Sample Number 04
Sample Description
110195-9Z4-01D 02 110195-924-01B 05 110195-924-01E 03 110195-924-01C
Certified By
110795 1638 copy617 890 3883 TMA-WALTHAM 003007
PRELIMINARY REPORT UNAUDITED RESULTS
Order f S5-11-034 Thermo Analytical Page 2 110795 1522 TEST RESULTS BY SAHPLE
Test Description Volatile Organics- Aqueous Method EPA_8240 Test Code Collected 110195 02-00 Category WATER
DATE INJECTED 110695 DILUTION FACTOR 100 All results reported 1n ugL
COMPOUND RESULT DET LIMIT COMPOUND RESULT
Chloromethane U 10 Broroodi chl oromethane U Vinyl Chloride U 10 2-Chloroethyl Vinyl Ether U
Bromxnethane U 10 4-dethyl -2-pentanone U Chloroethane U 10 c1 3-1 3-Di chl oropropene U
Trichlorofluoronwthane U 50 Tol uene U Acetone 17 10 trans-1 3-Di chl oropropene LI
11-Oichloroethene U 50 11 2-Tri chl oroethane J Carbon Dlsulfide U 50 2-Hexanone U
Methyl ene Chloride U 50 Tetrachl oroethene U 12-Oichloroethene (total) U 50 D1 bromochl oromethane U
11-01 Chloroethane U 50 Chlorobenzene U Vinyl Acetate U 10 Ethyl benzene U
2-Butanone U 10 in and p-Xylene U Chloroform U 50 o-Xylene U
111-Tri Chloroethane U 50 Styrene U Carbon Tetrachlortde U 50 Broraoform U
Benzene U 50 112 2-Tat rachl oroethane U 12-01 Chloroethane U 50 1 3-01 chl orobenzene U
Trichloroethene U 50 I 4-Di chl orobenzene U 12-Dichloropropane U 50 12-01 chl orobenzene U
SURROGATE STANDARDS RESULT LEVEL X RECOVERY
12-Dichloroethane-D4 52 50 104 Toluene-08 47 50 94
l-Bromo-4-fluorobenzene 56 50 112
NOTES AND DEFINITIONS FOR THIS REPORT U =bull Undetected at stated detection limit
VOAJI
OET LIMIT
50 50
10 50 50 50 50 10
5 0 50 5 0 5 0 50 50 50 50 50 50 50 50
110795 1639 copy617 890 3883 TMA-WALTHAM copy004007
PRELIMINARY REPORT UNAUDITED RESULTS
Order t S5-11-034 Thermo Analytical Page 4 110795 1522 TEST RESULTS BY SAMPLE
ianple Description 110195-924-010 Lab No 04A Test Description RCRA Metals 1n Water Method SW846 Test Code
Collected 110195 0200 Category WATER
METAL RESULT DETECTION LIMIT METAL RESULT DETECTION LIMIT
Ag Silver U 10 As Arsenic 870 50
Ba Bar inn B69 10 Pb Lead U 50
Cd Cadmium U 50 Se Sel en1 um Z15 50
Cr Chromi um U 20 Hg Mercury U 020
NOTES AND DEFINITIONS FOR THIS REPORT All results reported in ugL U gt Undetected at stated detection limit
110795 1640 Q617 890 3883 TMA-WALTHAM 0005007
PRELIMINARY REPORT UNAUDITED RESULTS
Order S5-11-034 Thermo Analytical Page 5 110795 1522 REGULAR TEST RESULTS BY TEST
Chemical Oxygen Demand Mlnimun Maximum Method EPA600 4101
Sap Sample Description Result Units Limit Prepared Analyzed By 05A 110195-924-01E 64 bullgL 50 110395 110395 JD
Petroleum Hydrocarbons-H20 Minimum Maximum Method EPA600 4181
Samp Sample Description Result Units Limit Prepared Analyzed By 01A 110195-924-01A 108 mgL 050 110395 110395 JO
110795 1640 reg617 890 3883 TMA-WALTHAM copy006007
PRELIMINARY REPORT UNAUDITED RESULTS
Order I S5-11-034 Therm Analytical Page 6 110795 1522 TEST METHODOLOGIES
USEPA Test Methods for Evaluating Solid Wastes (SUS46 Third Edition) Method 7470 - Preparation of water for Mercury analysis
USEPA Test Methods for Evaluating Solid Vastes (SW846 Third Edition) Method 3010 - Add digestion of aqueous samples and extracts for total metals for analysis by Flame Atomic Absorption Spectroscopy or Inductively Coupled Plasma Spectroscopy
USEPA Test Methods for Evaluating Solid Vastes (SWB46 Third Edition Method 8270 mdash Gas ChroroatographyMass Spectrometry for PAHs
Volatile Organics in Water - Hazardous Substance List
SV846 Method 8240 - Modified
Test Methods for Evaluating Solid Waste SU-846 US EPA Office of Solid Waste and Emergency Response Washington 3rd Edition
Aqueous sanples are analyzed in accordance with Method 8240 using a purge and trap technique followed by 64s ChromatographyMass Spectroscopy
Quality assurance procedures for GCMS Include daily tuning and calibration of the mass spectrometer and the use of surrogate standards in each sample to monitor method performance Quantitatton is performed by the Internal standard method Analysis of blanks duplicate samples and standards are run frequently as further quality assurance procedures
USEPA Test Methods for Evaluating Solid Wastes (SW846 Third Edition) Method 3S10 mdash Separatory Funnel Liquid-Liquid Extraction
EPA-6004-79-020 - Chemical Oxygen Demand - Titrimetric Mid-Level Method 4101
EPA6004-79-020 - Petroleum Hydrocarbons 1n Water Total Recoverable Method 4181 (Spectrophotometric Infrared)
110795 1641 copy617 890 3883 TMA-WALTHAM copy007007
APPENDIX B
QUANTITY SURVEY DOCUMENTATION
TFMORAN INC Surveying - Engineering - Land Planning SoilsWetlands Mapping - Landscape Architecture
January 15 1996
Mr Jack Enos Vice President TFord Company Inc 118 Tenney Street Georgetown MA 01833
RE Survey Results - Salem Acres - SL4 Area Salem Massachusetts
Dear Jack
This letter amends the letter of December 13 1995 per our review last week
TFMoran Inc performed topographic surveys at the Salem Acres site on April 21 1994 for GEI Consultants prior to removal of material and for TFord Company on October 18 1995 after the removal of material The survey data from the original survey in 1994 was adjusted thirty feet higher to correct for a datum difference from current site datum This was due to the original reporting of the Site Benchmark (TP34) elevation as 11464 rather than 14464 which is the correct elevation
Once both topographic surfaces were on the site datum the raw cut volume was obtained by Eaglepoint (Volumes Module) Software utilizing the prismoidal method comparing the two surfaces For reference please see the attached topographic plan which superimposes the October 15 1995 contours (dark lines) over the April 21 1994 contours The volume is based on the intersection of the two surfaces Also it was noted that stock piles of material did exist on site which were not surveyed at the time
The final raw cut volume arrived at by the above methods is 12749 Cubic Yards
In November and December of 1995 the site was resurveyed to locate the area of exposed ledge at the site The results of this survey are shown on the attached topographic worksheet dated November 3 1995 and last revised January 15 1996 The results of the survey indicate the total site area to be 50860 sq ft or 117 acres The total area of exposed ledge surveyed is 19990 sq ft or 46 acres If you have any questions regarding the above call me directly Thank you
Sincerely
John W Myhaver Jr ^_ Field Operations Manager
Enclosure ItorLltr
Route 101 Bedford NH 03110 Phone (603) 472-4488 FAX (603) 472-9747
APPENDIX C
HEALTH AND SAFETY PHASE-OUT REPORT
HEALTH AND SAFETY PHASE-OUT REPORT SALEM ACRES SL-4 AREA
Introduction
During remediation work on SL-4 Health and Safety Monitoring was performed Cashins amp Associates Inc of Reading MA performed the following work as a subcontractor to TFCI
1) Preparation of a site-specific Health and Safety Plan (dated September 1 1995)
2) Provide a Field TechnicianIndustrial Hygienist to serve as Site Safety and Health Officer (SSHO) and to conduct air and noise monitoring
3) Provide a Certified Industrial Hygienist to review Health and Safety and to conduct site specific training (record of training included at end of Appendix C)
4) Collect 8-hour air samples for worker exposure and ambient air at the Barcelona Avenue gate Arrange for analysis of the samples and report results
5) Prepare daily and weekly Health and Safety reports
6) Prepare a Health and Safety Phase-Out Report
In general the following health and safety practices were followed
1) All workers wore hard hats safety glasses work boots gloves and hearing protection as minimum level PPE
2) When working in the exclusion zone workers wore in addition to above tyvek rubber overboots and rubber coated gloves When dust was a potential concern an industrial grade dustmist mask was also worn This level of PPE was considered Level D modified
3) Workers leaving the exclusion zone removed PPE (tyveks gloves boots and masks) in the support zone and either disposed of the items or decontaminated them
4) Workers andor visitors without 40-hour OSHA training were not permitted to enter the exclusion zone
Attached is a report prepared by Cashins amp Associates along with weekly Health and Safety Summary Reports prepared by the Field Hygienist In summary the air monitoring results indicate no levels exceeding the applicable exposure guidelines except one instance
During excavation of contaminated overburden in the northwest comer of the site an area of VOC contaminated soil was encountered Total VOCs levels measured using a PID exceeded the action level established in the Health and Safety Plan The SSHO advised TFCI to upgrade to Level C PPE in order to backfill the excavation in this area TFCI equipment operator upgraded and backfilled the area The SSHO in consultation with the Cashins CIH advised TFCI to avoid work in this area until the contaminants were characterized GEI sampled the material for waste characterization analysis and provided the results to TFCI Based on the results an action level was established by the CIH for the specific contaminants found Further PID measurements indicated levels below the new action level and work was resumed
The noise monitoring indicated that the noise level at the Barcelona Avenue gate was not exceeded Only one instance of excess noise level in the work zone was recorded (10 db(a) above the ambient noise level or 85 db(a)) Workers wore hearing protection in this instance
mdash 07171996 1601 6179444032 CASHIMS S ASSOCIATES PAGE 02
CASHINS amp Associates Inc
ItxhalrM Hy-gifnr A Invtronmtnltl Tttling
July 17 1996
Mr Jack Enos T Ford Company Inc USTenney Street Georgetown MA 01833
Dear Jack
The Site Safety and Health Officer (SSHO) from Cashing amp Associates Inc performed daily inspections of the SL-4 area Salem Acres Superfund Site between 9595 and 12195 in accordance with the Health amp Safety Plan (HSP) for the site Daily inspection logs were submitted every day No accidentsincidents were reported during the work period
In accordance with the Health amp Safety Plan the SSHO performed daily air and noise monitoring at the site during Ac project Samples were collected for metals (lead beryllium chromium arsenic) and Polynuclear Aromatic Hydrocarbons (PAHs) at the site perimeter and for workers exposure determination Coal Tar Pitch Volatiles (a benzene soluble extractables) were also used to determine the workers exposure to PAH compounds Coal Tar Pitch Volatiles (CTPV) were analyzed using OSHA 58 Method If CTPV levels oq personal samples exceed the site criteria of 02 ragm3 the sample was submitted for PAHs analysis All air samples on the site perimeter were analyzed for PAH compounds
Site monitoring air sample collection and results report were done under the supervision of a Certified Industrial Hygienist
Full shift personal worker exposure samples were collected once a week Ambient air samples were collected at the Barcelona Avenue gate about 20 feet to the west of the site gate to determine if site contaminants were migrating off site The ambient air samples were also collected once a week during the project except on rainy days and days without work with contaminated soil
All air samples were analyzed by the American Industrial Hygiene Association accredited ESA Laboratories Inc using the following methods PAHs - NIOSH 5515 Lead - NIOSH 7082 Beryllium - NIOSH 7102 Chromium - NIOSH 7024 Arsenic - NIOSH 7900 Coal Tar Pitch Volatiles - OSHA 58 All methods used are accepted by the industrial hygiene community for 8-hour exposure assessment EPA methods are usually used for ambient air measurements
CRErORTTFOmiOO
80 Mam Street bull Reading MA 01867 bull Phone- 61 7-944-4060 bull Fax 61 7-944-4082
07171996 1601 6179444032 CASHIMS amp ASSOCIATES PAGE 03
The results of air samples for metals and PAHs are presented in Table No 1
All concentrations of metals and PAHs at the site perimeter (Barcelona Avenue) and active work zones were below the OSHA Permissible Exposure Limits (PEL) and the American Conference of Governmental Industrial Hygicnists Threshold Limit Value (ACGIH TLV) Two personal samples collected on October 19 and October 23rd showed Coal Tar Pitch Volatiles (CTPV) results above OSHA PEL and AIHA TLV limits Both samples were resubmittcd to the lab for further analysis to determine if PAH compounds are present because the CTPV results were above site criteria
The results of the PAH concentrations for the personal sample on Mark Goodwin on October 19 1995 during excavation and washing trucks and for the personal sample on Ron Maker on October 23 1995 during excavating and cleaning rocks by compressed air were below OSHA PEL and ACGIH TLV limits
The SSHO performed noise monitoring according to the HSP at the exclusion zone and at the Barcelona Avenue site perimeter fence A Dupont sound level meter was used for noise monitoring The noise level in the exclusion zone during all operations except one did not exceed the on site criteria of 85 dB(a) During a short time when the air compressor had been used to clean rocks the sound level in the exclusion zone next to the air compressor did exceed 85 dB(a) Ear protection devices were worn by the workers during that operation At no time did the noise level at the Barcelona Avenue site perimeter exceed 10 dB(a) above the ambient noise level or 85 dB(a)
The SSHO performed total dust monitoring on a daily basis during the project at the site perimeter downwind of work location and at the site gate using a Miniram real time dust meter The summary of dust monitoring is presented in Table No 2 Total dust concentrations on site and off site did not exceed site criteria of 1 mgm3 and the action level of 05 nigny1
The summary of air monitoring for Volatile Organic Compounds (VOC) is presented in Table No 3 VOC concentrations in the working area did not exceed the on site criteria of 5 ppm in a breathing zone VOC concentrations on the site perimeter did not exceed real time off site criteria of 2 ppm
Five detail reports with results of air sampling were submitted during the project period
Sincerely Cashins amp Associates Inc
Evelina Vaughan Industrial Hygieflfst
CASHINS amp ASSOCIATES Inc
80 Mam Street bull Reading MA 01867 bull Phone61 7-944-4060 bull Fax 617-944-4082
07171996 1601 6179444082 CASHINS S ASSOCIATES PAGE 04
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SITE SPECIFIC amp HAZARD COMMUNICATIONS TRAINING SIGN-IN SHEET
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OSHINSamp Associates Inc
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89111995 1023 6172733(384 CASHINS ASSOCIATES PAGE 01
CASHINS amp Associates inc
Ifxtuitral Hygltne A fnvironmtnltt Tuning
W3SXLY HBALTH amp SAFETY PLAN COMPLIANCE SUMMARY R3PORT
CLIENT T foyd C o m a n
LOCATION gal era Acres Sx^perfund Site 8L-4 Area
DATES INCLUDED IN SUMMARY
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SUMMARIZED BY FOR CASHINS amp ASSOCIATES INC
55 CAMBRIDGE STREET bull SUITE 201 bull BURLINGTON MA 01803 laquo TEL 61 -273-9080 bull FAX 67-273-9C84
09111995 1023 6172739084 CASHINS ASSOCIATES PAGE 01
CASHINSamp Associates Inc
Induttrml Hygttnr t Emtroomtnttl Ttstinf
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Fprd Company
LOCATION Salen Acres Suoerfund Site SL-4 Area
DATES INCLUDED IN SUMMARY
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CASHINS amp Associates Inc
Industrial Hygitnf amp CmimnmenUl Tinting
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Compan
LOCATION Salem Acres Superfund Site SL-4 Area
DATES INCLUDED IN SUMMARY
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CASHING X ASSOCIATES PAGE
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WEEKLY HEALTH amp SAFBTT PLAN COMPLIANCE SUMMARY REPORT
CLIENT ^T Ford Combanv
LOCATION Salam Aerag SL-4
DATES INCLUDED IN SUMMARY
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CASHINSamp Associates Inc
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WEEKLY HEALTH 6 SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Fortjl Cqjapany
LOCATION Salem Acrlaquoa Superfund Site 9L-4 Area
DATES INCLUDED IN SUMMARY
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OSHINSamp Associates Inc
Industrial Hygiene amp Emironmvntal Testing
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Company
LOCATION Salem Acres Superfund Site SL-4 Area
DATES INCLUDED IN SUMMARY J_
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Industrial Hygifnr amp [nvironmenljl res
SERIOUS HAZARD NOTIFICATION
ISSUED TO REPRESENTING
ISSUED BY REPRESENTING CASHINS S ASSOCIATES INcT DAY DATE ISSUED O04Xmdash 1 bull-bullmdashbull f P^JT
PROJECT NAME_ SITE LOCATION
THE PURPOSE OF THE FOLLOWING STATEMENT IS TO DOCUMENT THE EXISTENCE OF A CONDITION OR CONCERN WHICH CASHINS amp ASSOCIATES INC BELIEVES WARRANTS IMMEDIATE CORRECTIVE ACTION POSSIBLE SOLUTIONS AND OR CORRECTIVE ACTIONS WILL BE INCLUDED IN THIS NOTIFICATION WHEN POSSIBLE THIS NOTIFICATION IS LIMITED TO SITUATIONS THAT REPRESENT EITHER IMMEDIATE DANGER TO LIFE OR HEALTH CONDITIONS OR PREVIOUSLY IDENTIFIED CHRONIC PROBLEMS THAT UNDERMINE OUR ABILITY TO EFFECTIVELY INSURE COMPLIANCE WITH THE REQUIREMENTS OF THE HEALTH AND SAFETY PLAN
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CISHINS amp Associates Inc
Industrial Hygirne amp Cmimnmtntal Testing
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Company
LOCATION Salem Acres Superfund Site SL-4 Area
DATES INCLUDED IN SUMMARY T
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WEEKLY HEALTH amp SA7STT PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Coqpanv
LOCATION Sa^am Acras Super fund 5 jte SL-4 Area
DATES INCLUDED IN SUMMARY bull
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LOCATION Salem Acraa Suoerfund Sita 5L-4
DATES INCLUDED IN SUMMARY bull
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07161996 1650 617944408 CASHING 3 ASSOCIATES PAGE 05
CASHINSamp Associates Inc
fmimnntattl few
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT t T Ford Coimbanv
LOCATION t Salam Acraa Suoarfund Site SL-4 Arlaquoa
DATES INCLUDED IN SUMMARYj pound mdashiffofrshy f
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CASHIMS amp ASSOCIATES PAGE 04 07161996 1658 6179444032
OVSHINSamp Associates Inc
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Company T
LOCATION Salem AcrM Suoerfund Stta 8L-4 Araa
DATES INCLUDED IN SUMMARY
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LOCATION Sal era Acraa Suplaquorfund Sj-ta 8L-4 Araa
DATES INCLUDED IN SUMMARY
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07151996 18 fO 6179444082 CASHINS S ASSOCIATES PAGE 02
CASHINS amp Associates Inc
WBBKLY HEALTH amp SAFETY FLAK COMPLIANCE SUMMARY REPORT
CLIENT T Ford Compapv
LOCATION i Sal am Acrlaquolaquo Suparfund Sita SL-4 Area
DATES INCLUDED IN SUMMARY i bull pound7 mdash
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- barcode 14732
- barcodetext SEMS Doc ID 14732
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VIEW OF BARCELONA AVENUE THROUGH ENTRANCE GATE PRECONT RUCTION
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(2)
VIEW OF ACCESS ROAD LOOKING NORTH SL-4 ON LEFT PRECONSTRUCTION
VIEW OF ACCESS ROAD LOOKING NORTH SL-4 ON LEFT DA-1 TO LEFT OF PICKUP TRUCK
PRECONSTRUCTION
(3)
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
O ID a CO z O OHI
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(5)
VIEW OF BOUNDARY BETWEEN SL-4 AND DA-1 LOOKING WEST PRECONSTRUCTION
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(6)
EROSION CONTROLS LOOKING NORTH FROM CORNER OF SL-4SL-5 ADJACENT TO WA-1 PRECONSTRUCTION
(7)
TRUCK LOADING PAD LOOKING NORTHWEST FROM SUPPORT ZONE
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(8)
DECONTAMINATION PAD LOOKING NORTHWEST FROM SUPPORT ZONE
(9)
EXCAVATION OF FLY ASH LOOKING NORTHWEST FROM CRZ NOTE WATER FOR DUST CONTROL
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(10)
VIEW LOOKING WEST AFTER REMOVAL OF FLY ASH NOTE WA-1 BEYOND EROSION CONTROLS
(11)
EXCAVATION OF CONTAMINATED OVERBURDEN LOOKING SOUTH FROM DA-1 BOUNDARY
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(12)
VIEW OF RESTORED SITE LOOKING WEST TOWARD WA-1
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ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(15)
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VIEW OF RESTORED SITE ON DA-1 SJDE OF FENCE - LOOKING ST
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(18)
VIEW OF RESTORED SITE ON DA-1 SIDE OF FENCE - LOOKING WEST SL-4 ON RIGHT
APPENDIX A
ANALYTICAL RESULTS FOR
PONDED WATER
110795 1638 copy617 890 3883 TMA-WALTHAM ] 002007
PRELIMINARY REPORT UNAUDITED RESULTS
Thenno Analytical 300 Second Avenue PO Box 521 Waltham HA 02254
Attn Client Services Phone (617) 890-7200
Cashins amp Associates Order S5-11-034 55 Cambridge Street Date 110795 1522 Burlington HA 01803 Work ID Salem Acres Water
Date Received 110295 Attn Bob Cashins Date Completed
Purchase Order NA Invoice Number Client Code CASHINS
SAMPLE IDENTIFICATION
Sample Sample Number Description 01 11019S-924-01A
Sample Number 04
Sample Description
110195-9Z4-01D 02 110195-924-01B 05 110195-924-01E 03 110195-924-01C
Certified By
110795 1638 copy617 890 3883 TMA-WALTHAM 003007
PRELIMINARY REPORT UNAUDITED RESULTS
Order f S5-11-034 Thermo Analytical Page 2 110795 1522 TEST RESULTS BY SAHPLE
Test Description Volatile Organics- Aqueous Method EPA_8240 Test Code Collected 110195 02-00 Category WATER
DATE INJECTED 110695 DILUTION FACTOR 100 All results reported 1n ugL
COMPOUND RESULT DET LIMIT COMPOUND RESULT
Chloromethane U 10 Broroodi chl oromethane U Vinyl Chloride U 10 2-Chloroethyl Vinyl Ether U
Bromxnethane U 10 4-dethyl -2-pentanone U Chloroethane U 10 c1 3-1 3-Di chl oropropene U
Trichlorofluoronwthane U 50 Tol uene U Acetone 17 10 trans-1 3-Di chl oropropene LI
11-Oichloroethene U 50 11 2-Tri chl oroethane J Carbon Dlsulfide U 50 2-Hexanone U
Methyl ene Chloride U 50 Tetrachl oroethene U 12-Oichloroethene (total) U 50 D1 bromochl oromethane U
11-01 Chloroethane U 50 Chlorobenzene U Vinyl Acetate U 10 Ethyl benzene U
2-Butanone U 10 in and p-Xylene U Chloroform U 50 o-Xylene U
111-Tri Chloroethane U 50 Styrene U Carbon Tetrachlortde U 50 Broraoform U
Benzene U 50 112 2-Tat rachl oroethane U 12-01 Chloroethane U 50 1 3-01 chl orobenzene U
Trichloroethene U 50 I 4-Di chl orobenzene U 12-Dichloropropane U 50 12-01 chl orobenzene U
SURROGATE STANDARDS RESULT LEVEL X RECOVERY
12-Dichloroethane-D4 52 50 104 Toluene-08 47 50 94
l-Bromo-4-fluorobenzene 56 50 112
NOTES AND DEFINITIONS FOR THIS REPORT U =bull Undetected at stated detection limit
VOAJI
OET LIMIT
50 50
10 50 50 50 50 10
5 0 50 5 0 5 0 50 50 50 50 50 50 50 50
110795 1639 copy617 890 3883 TMA-WALTHAM copy004007
PRELIMINARY REPORT UNAUDITED RESULTS
Order t S5-11-034 Thermo Analytical Page 4 110795 1522 TEST RESULTS BY SAMPLE
ianple Description 110195-924-010 Lab No 04A Test Description RCRA Metals 1n Water Method SW846 Test Code
Collected 110195 0200 Category WATER
METAL RESULT DETECTION LIMIT METAL RESULT DETECTION LIMIT
Ag Silver U 10 As Arsenic 870 50
Ba Bar inn B69 10 Pb Lead U 50
Cd Cadmium U 50 Se Sel en1 um Z15 50
Cr Chromi um U 20 Hg Mercury U 020
NOTES AND DEFINITIONS FOR THIS REPORT All results reported in ugL U gt Undetected at stated detection limit
110795 1640 Q617 890 3883 TMA-WALTHAM 0005007
PRELIMINARY REPORT UNAUDITED RESULTS
Order S5-11-034 Thermo Analytical Page 5 110795 1522 REGULAR TEST RESULTS BY TEST
Chemical Oxygen Demand Mlnimun Maximum Method EPA600 4101
Sap Sample Description Result Units Limit Prepared Analyzed By 05A 110195-924-01E 64 bullgL 50 110395 110395 JD
Petroleum Hydrocarbons-H20 Minimum Maximum Method EPA600 4181
Samp Sample Description Result Units Limit Prepared Analyzed By 01A 110195-924-01A 108 mgL 050 110395 110395 JO
110795 1640 reg617 890 3883 TMA-WALTHAM copy006007
PRELIMINARY REPORT UNAUDITED RESULTS
Order I S5-11-034 Therm Analytical Page 6 110795 1522 TEST METHODOLOGIES
USEPA Test Methods for Evaluating Solid Wastes (SUS46 Third Edition) Method 7470 - Preparation of water for Mercury analysis
USEPA Test Methods for Evaluating Solid Vastes (SW846 Third Edition) Method 3010 - Add digestion of aqueous samples and extracts for total metals for analysis by Flame Atomic Absorption Spectroscopy or Inductively Coupled Plasma Spectroscopy
USEPA Test Methods for Evaluating Solid Vastes (SWB46 Third Edition Method 8270 mdash Gas ChroroatographyMass Spectrometry for PAHs
Volatile Organics in Water - Hazardous Substance List
SV846 Method 8240 - Modified
Test Methods for Evaluating Solid Waste SU-846 US EPA Office of Solid Waste and Emergency Response Washington 3rd Edition
Aqueous sanples are analyzed in accordance with Method 8240 using a purge and trap technique followed by 64s ChromatographyMass Spectroscopy
Quality assurance procedures for GCMS Include daily tuning and calibration of the mass spectrometer and the use of surrogate standards in each sample to monitor method performance Quantitatton is performed by the Internal standard method Analysis of blanks duplicate samples and standards are run frequently as further quality assurance procedures
USEPA Test Methods for Evaluating Solid Wastes (SW846 Third Edition) Method 3S10 mdash Separatory Funnel Liquid-Liquid Extraction
EPA-6004-79-020 - Chemical Oxygen Demand - Titrimetric Mid-Level Method 4101
EPA6004-79-020 - Petroleum Hydrocarbons 1n Water Total Recoverable Method 4181 (Spectrophotometric Infrared)
110795 1641 copy617 890 3883 TMA-WALTHAM copy007007
APPENDIX B
QUANTITY SURVEY DOCUMENTATION
TFMORAN INC Surveying - Engineering - Land Planning SoilsWetlands Mapping - Landscape Architecture
January 15 1996
Mr Jack Enos Vice President TFord Company Inc 118 Tenney Street Georgetown MA 01833
RE Survey Results - Salem Acres - SL4 Area Salem Massachusetts
Dear Jack
This letter amends the letter of December 13 1995 per our review last week
TFMoran Inc performed topographic surveys at the Salem Acres site on April 21 1994 for GEI Consultants prior to removal of material and for TFord Company on October 18 1995 after the removal of material The survey data from the original survey in 1994 was adjusted thirty feet higher to correct for a datum difference from current site datum This was due to the original reporting of the Site Benchmark (TP34) elevation as 11464 rather than 14464 which is the correct elevation
Once both topographic surfaces were on the site datum the raw cut volume was obtained by Eaglepoint (Volumes Module) Software utilizing the prismoidal method comparing the two surfaces For reference please see the attached topographic plan which superimposes the October 15 1995 contours (dark lines) over the April 21 1994 contours The volume is based on the intersection of the two surfaces Also it was noted that stock piles of material did exist on site which were not surveyed at the time
The final raw cut volume arrived at by the above methods is 12749 Cubic Yards
In November and December of 1995 the site was resurveyed to locate the area of exposed ledge at the site The results of this survey are shown on the attached topographic worksheet dated November 3 1995 and last revised January 15 1996 The results of the survey indicate the total site area to be 50860 sq ft or 117 acres The total area of exposed ledge surveyed is 19990 sq ft or 46 acres If you have any questions regarding the above call me directly Thank you
Sincerely
John W Myhaver Jr ^_ Field Operations Manager
Enclosure ItorLltr
Route 101 Bedford NH 03110 Phone (603) 472-4488 FAX (603) 472-9747
APPENDIX C
HEALTH AND SAFETY PHASE-OUT REPORT
HEALTH AND SAFETY PHASE-OUT REPORT SALEM ACRES SL-4 AREA
Introduction
During remediation work on SL-4 Health and Safety Monitoring was performed Cashins amp Associates Inc of Reading MA performed the following work as a subcontractor to TFCI
1) Preparation of a site-specific Health and Safety Plan (dated September 1 1995)
2) Provide a Field TechnicianIndustrial Hygienist to serve as Site Safety and Health Officer (SSHO) and to conduct air and noise monitoring
3) Provide a Certified Industrial Hygienist to review Health and Safety and to conduct site specific training (record of training included at end of Appendix C)
4) Collect 8-hour air samples for worker exposure and ambient air at the Barcelona Avenue gate Arrange for analysis of the samples and report results
5) Prepare daily and weekly Health and Safety reports
6) Prepare a Health and Safety Phase-Out Report
In general the following health and safety practices were followed
1) All workers wore hard hats safety glasses work boots gloves and hearing protection as minimum level PPE
2) When working in the exclusion zone workers wore in addition to above tyvek rubber overboots and rubber coated gloves When dust was a potential concern an industrial grade dustmist mask was also worn This level of PPE was considered Level D modified
3) Workers leaving the exclusion zone removed PPE (tyveks gloves boots and masks) in the support zone and either disposed of the items or decontaminated them
4) Workers andor visitors without 40-hour OSHA training were not permitted to enter the exclusion zone
Attached is a report prepared by Cashins amp Associates along with weekly Health and Safety Summary Reports prepared by the Field Hygienist In summary the air monitoring results indicate no levels exceeding the applicable exposure guidelines except one instance
During excavation of contaminated overburden in the northwest comer of the site an area of VOC contaminated soil was encountered Total VOCs levels measured using a PID exceeded the action level established in the Health and Safety Plan The SSHO advised TFCI to upgrade to Level C PPE in order to backfill the excavation in this area TFCI equipment operator upgraded and backfilled the area The SSHO in consultation with the Cashins CIH advised TFCI to avoid work in this area until the contaminants were characterized GEI sampled the material for waste characterization analysis and provided the results to TFCI Based on the results an action level was established by the CIH for the specific contaminants found Further PID measurements indicated levels below the new action level and work was resumed
The noise monitoring indicated that the noise level at the Barcelona Avenue gate was not exceeded Only one instance of excess noise level in the work zone was recorded (10 db(a) above the ambient noise level or 85 db(a)) Workers wore hearing protection in this instance
mdash 07171996 1601 6179444032 CASHIMS S ASSOCIATES PAGE 02
CASHINS amp Associates Inc
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July 17 1996
Mr Jack Enos T Ford Company Inc USTenney Street Georgetown MA 01833
Dear Jack
The Site Safety and Health Officer (SSHO) from Cashing amp Associates Inc performed daily inspections of the SL-4 area Salem Acres Superfund Site between 9595 and 12195 in accordance with the Health amp Safety Plan (HSP) for the site Daily inspection logs were submitted every day No accidentsincidents were reported during the work period
In accordance with the Health amp Safety Plan the SSHO performed daily air and noise monitoring at the site during Ac project Samples were collected for metals (lead beryllium chromium arsenic) and Polynuclear Aromatic Hydrocarbons (PAHs) at the site perimeter and for workers exposure determination Coal Tar Pitch Volatiles (a benzene soluble extractables) were also used to determine the workers exposure to PAH compounds Coal Tar Pitch Volatiles (CTPV) were analyzed using OSHA 58 Method If CTPV levels oq personal samples exceed the site criteria of 02 ragm3 the sample was submitted for PAHs analysis All air samples on the site perimeter were analyzed for PAH compounds
Site monitoring air sample collection and results report were done under the supervision of a Certified Industrial Hygienist
Full shift personal worker exposure samples were collected once a week Ambient air samples were collected at the Barcelona Avenue gate about 20 feet to the west of the site gate to determine if site contaminants were migrating off site The ambient air samples were also collected once a week during the project except on rainy days and days without work with contaminated soil
All air samples were analyzed by the American Industrial Hygiene Association accredited ESA Laboratories Inc using the following methods PAHs - NIOSH 5515 Lead - NIOSH 7082 Beryllium - NIOSH 7102 Chromium - NIOSH 7024 Arsenic - NIOSH 7900 Coal Tar Pitch Volatiles - OSHA 58 All methods used are accepted by the industrial hygiene community for 8-hour exposure assessment EPA methods are usually used for ambient air measurements
CRErORTTFOmiOO
80 Mam Street bull Reading MA 01867 bull Phone- 61 7-944-4060 bull Fax 61 7-944-4082
07171996 1601 6179444032 CASHIMS amp ASSOCIATES PAGE 03
The results of air samples for metals and PAHs are presented in Table No 1
All concentrations of metals and PAHs at the site perimeter (Barcelona Avenue) and active work zones were below the OSHA Permissible Exposure Limits (PEL) and the American Conference of Governmental Industrial Hygicnists Threshold Limit Value (ACGIH TLV) Two personal samples collected on October 19 and October 23rd showed Coal Tar Pitch Volatiles (CTPV) results above OSHA PEL and AIHA TLV limits Both samples were resubmittcd to the lab for further analysis to determine if PAH compounds are present because the CTPV results were above site criteria
The results of the PAH concentrations for the personal sample on Mark Goodwin on October 19 1995 during excavation and washing trucks and for the personal sample on Ron Maker on October 23 1995 during excavating and cleaning rocks by compressed air were below OSHA PEL and ACGIH TLV limits
The SSHO performed noise monitoring according to the HSP at the exclusion zone and at the Barcelona Avenue site perimeter fence A Dupont sound level meter was used for noise monitoring The noise level in the exclusion zone during all operations except one did not exceed the on site criteria of 85 dB(a) During a short time when the air compressor had been used to clean rocks the sound level in the exclusion zone next to the air compressor did exceed 85 dB(a) Ear protection devices were worn by the workers during that operation At no time did the noise level at the Barcelona Avenue site perimeter exceed 10 dB(a) above the ambient noise level or 85 dB(a)
The SSHO performed total dust monitoring on a daily basis during the project at the site perimeter downwind of work location and at the site gate using a Miniram real time dust meter The summary of dust monitoring is presented in Table No 2 Total dust concentrations on site and off site did not exceed site criteria of 1 mgm3 and the action level of 05 nigny1
The summary of air monitoring for Volatile Organic Compounds (VOC) is presented in Table No 3 VOC concentrations in the working area did not exceed the on site criteria of 5 ppm in a breathing zone VOC concentrations on the site perimeter did not exceed real time off site criteria of 2 ppm
Five detail reports with results of air sampling were submitted during the project period
Sincerely Cashins amp Associates Inc
Evelina Vaughan Industrial Hygieflfst
CASHINS amp ASSOCIATES Inc
80 Mam Street bull Reading MA 01867 bull Phone61 7-944-4060 bull Fax 617-944-4082
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ISSUED BY REPRESENTING CASHINS S ASSOCIATES INcT DAY DATE ISSUED O04Xmdash 1 bull-bullmdashbull f P^JT
PROJECT NAME_ SITE LOCATION
THE PURPOSE OF THE FOLLOWING STATEMENT IS TO DOCUMENT THE EXISTENCE OF A CONDITION OR CONCERN WHICH CASHINS amp ASSOCIATES INC BELIEVES WARRANTS IMMEDIATE CORRECTIVE ACTION POSSIBLE SOLUTIONS AND OR CORRECTIVE ACTIONS WILL BE INCLUDED IN THIS NOTIFICATION WHEN POSSIBLE THIS NOTIFICATION IS LIMITED TO SITUATIONS THAT REPRESENT EITHER IMMEDIATE DANGER TO LIFE OR HEALTH CONDITIONS OR PREVIOUSLY IDENTIFIED CHRONIC PROBLEMS THAT UNDERMINE OUR ABILITY TO EFFECTIVELY INSURE COMPLIANCE WITH THE REQUIREMENTS OF THE HEALTH AND SAFETY PLAN
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CASHIMS amp ASSOCIATES PAGE 04 07161996 1658 6179444032
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CLIENT T Ford Company T
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CASHINS amp Associates Inc
WBBKLY HEALTH amp SAFETY FLAK COMPLIANCE SUMMARY REPORT
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- barcode 14732
- barcodetext SEMS Doc ID 14732
![Page 20: SALEM ACRES SUPERFUND SITE SALEM, MA ...The truck loading pa d consisted of a crushed stone are sea t up along the east sid e o f SL-4 adjacent to the access road A. row of concrete](https://reader036.vdocuments.us/reader036/viewer/2022070114/60729b840fec4e6b4d136a16/html5/thumbnails/20.jpg)
VIEW OF ACCESS ROAD LOOKING NORTH SL-4 ON LEFT DA-1 TO LEFT OF PICKUP TRUCK
PRECONSTRUCTION
(3)
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
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VIEW OF BOUNDARY BETWEEN SL-4 AND DA-1 LOOKING WEST PRECONSTRUCTION
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(6)
EROSION CONTROLS LOOKING NORTH FROM CORNER OF SL-4SL-5 ADJACENT TO WA-1 PRECONSTRUCTION
(7)
TRUCK LOADING PAD LOOKING NORTHWEST FROM SUPPORT ZONE
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(8)
DECONTAMINATION PAD LOOKING NORTHWEST FROM SUPPORT ZONE
(9)
EXCAVATION OF FLY ASH LOOKING NORTHWEST FROM CRZ NOTE WATER FOR DUST CONTROL
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(10)
VIEW LOOKING WEST AFTER REMOVAL OF FLY ASH NOTE WA-1 BEYOND EROSION CONTROLS
(11)
EXCAVATION OF CONTAMINATED OVERBURDEN LOOKING SOUTH FROM DA-1 BOUNDARY
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(12)
VIEW OF RESTORED SITE LOOKING WEST TOWARD WA-1
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ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
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ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(18)
VIEW OF RESTORED SITE ON DA-1 SIDE OF FENCE - LOOKING WEST SL-4 ON RIGHT
APPENDIX A
ANALYTICAL RESULTS FOR
PONDED WATER
110795 1638 copy617 890 3883 TMA-WALTHAM ] 002007
PRELIMINARY REPORT UNAUDITED RESULTS
Thenno Analytical 300 Second Avenue PO Box 521 Waltham HA 02254
Attn Client Services Phone (617) 890-7200
Cashins amp Associates Order S5-11-034 55 Cambridge Street Date 110795 1522 Burlington HA 01803 Work ID Salem Acres Water
Date Received 110295 Attn Bob Cashins Date Completed
Purchase Order NA Invoice Number Client Code CASHINS
SAMPLE IDENTIFICATION
Sample Sample Number Description 01 11019S-924-01A
Sample Number 04
Sample Description
110195-9Z4-01D 02 110195-924-01B 05 110195-924-01E 03 110195-924-01C
Certified By
110795 1638 copy617 890 3883 TMA-WALTHAM 003007
PRELIMINARY REPORT UNAUDITED RESULTS
Order f S5-11-034 Thermo Analytical Page 2 110795 1522 TEST RESULTS BY SAHPLE
Test Description Volatile Organics- Aqueous Method EPA_8240 Test Code Collected 110195 02-00 Category WATER
DATE INJECTED 110695 DILUTION FACTOR 100 All results reported 1n ugL
COMPOUND RESULT DET LIMIT COMPOUND RESULT
Chloromethane U 10 Broroodi chl oromethane U Vinyl Chloride U 10 2-Chloroethyl Vinyl Ether U
Bromxnethane U 10 4-dethyl -2-pentanone U Chloroethane U 10 c1 3-1 3-Di chl oropropene U
Trichlorofluoronwthane U 50 Tol uene U Acetone 17 10 trans-1 3-Di chl oropropene LI
11-Oichloroethene U 50 11 2-Tri chl oroethane J Carbon Dlsulfide U 50 2-Hexanone U
Methyl ene Chloride U 50 Tetrachl oroethene U 12-Oichloroethene (total) U 50 D1 bromochl oromethane U
11-01 Chloroethane U 50 Chlorobenzene U Vinyl Acetate U 10 Ethyl benzene U
2-Butanone U 10 in and p-Xylene U Chloroform U 50 o-Xylene U
111-Tri Chloroethane U 50 Styrene U Carbon Tetrachlortde U 50 Broraoform U
Benzene U 50 112 2-Tat rachl oroethane U 12-01 Chloroethane U 50 1 3-01 chl orobenzene U
Trichloroethene U 50 I 4-Di chl orobenzene U 12-Dichloropropane U 50 12-01 chl orobenzene U
SURROGATE STANDARDS RESULT LEVEL X RECOVERY
12-Dichloroethane-D4 52 50 104 Toluene-08 47 50 94
l-Bromo-4-fluorobenzene 56 50 112
NOTES AND DEFINITIONS FOR THIS REPORT U =bull Undetected at stated detection limit
VOAJI
OET LIMIT
50 50
10 50 50 50 50 10
5 0 50 5 0 5 0 50 50 50 50 50 50 50 50
110795 1639 copy617 890 3883 TMA-WALTHAM copy004007
PRELIMINARY REPORT UNAUDITED RESULTS
Order t S5-11-034 Thermo Analytical Page 4 110795 1522 TEST RESULTS BY SAMPLE
ianple Description 110195-924-010 Lab No 04A Test Description RCRA Metals 1n Water Method SW846 Test Code
Collected 110195 0200 Category WATER
METAL RESULT DETECTION LIMIT METAL RESULT DETECTION LIMIT
Ag Silver U 10 As Arsenic 870 50
Ba Bar inn B69 10 Pb Lead U 50
Cd Cadmium U 50 Se Sel en1 um Z15 50
Cr Chromi um U 20 Hg Mercury U 020
NOTES AND DEFINITIONS FOR THIS REPORT All results reported in ugL U gt Undetected at stated detection limit
110795 1640 Q617 890 3883 TMA-WALTHAM 0005007
PRELIMINARY REPORT UNAUDITED RESULTS
Order S5-11-034 Thermo Analytical Page 5 110795 1522 REGULAR TEST RESULTS BY TEST
Chemical Oxygen Demand Mlnimun Maximum Method EPA600 4101
Sap Sample Description Result Units Limit Prepared Analyzed By 05A 110195-924-01E 64 bullgL 50 110395 110395 JD
Petroleum Hydrocarbons-H20 Minimum Maximum Method EPA600 4181
Samp Sample Description Result Units Limit Prepared Analyzed By 01A 110195-924-01A 108 mgL 050 110395 110395 JO
110795 1640 reg617 890 3883 TMA-WALTHAM copy006007
PRELIMINARY REPORT UNAUDITED RESULTS
Order I S5-11-034 Therm Analytical Page 6 110795 1522 TEST METHODOLOGIES
USEPA Test Methods for Evaluating Solid Wastes (SUS46 Third Edition) Method 7470 - Preparation of water for Mercury analysis
USEPA Test Methods for Evaluating Solid Vastes (SW846 Third Edition) Method 3010 - Add digestion of aqueous samples and extracts for total metals for analysis by Flame Atomic Absorption Spectroscopy or Inductively Coupled Plasma Spectroscopy
USEPA Test Methods for Evaluating Solid Vastes (SWB46 Third Edition Method 8270 mdash Gas ChroroatographyMass Spectrometry for PAHs
Volatile Organics in Water - Hazardous Substance List
SV846 Method 8240 - Modified
Test Methods for Evaluating Solid Waste SU-846 US EPA Office of Solid Waste and Emergency Response Washington 3rd Edition
Aqueous sanples are analyzed in accordance with Method 8240 using a purge and trap technique followed by 64s ChromatographyMass Spectroscopy
Quality assurance procedures for GCMS Include daily tuning and calibration of the mass spectrometer and the use of surrogate standards in each sample to monitor method performance Quantitatton is performed by the Internal standard method Analysis of blanks duplicate samples and standards are run frequently as further quality assurance procedures
USEPA Test Methods for Evaluating Solid Wastes (SW846 Third Edition) Method 3S10 mdash Separatory Funnel Liquid-Liquid Extraction
EPA-6004-79-020 - Chemical Oxygen Demand - Titrimetric Mid-Level Method 4101
EPA6004-79-020 - Petroleum Hydrocarbons 1n Water Total Recoverable Method 4181 (Spectrophotometric Infrared)
110795 1641 copy617 890 3883 TMA-WALTHAM copy007007
APPENDIX B
QUANTITY SURVEY DOCUMENTATION
TFMORAN INC Surveying - Engineering - Land Planning SoilsWetlands Mapping - Landscape Architecture
January 15 1996
Mr Jack Enos Vice President TFord Company Inc 118 Tenney Street Georgetown MA 01833
RE Survey Results - Salem Acres - SL4 Area Salem Massachusetts
Dear Jack
This letter amends the letter of December 13 1995 per our review last week
TFMoran Inc performed topographic surveys at the Salem Acres site on April 21 1994 for GEI Consultants prior to removal of material and for TFord Company on October 18 1995 after the removal of material The survey data from the original survey in 1994 was adjusted thirty feet higher to correct for a datum difference from current site datum This was due to the original reporting of the Site Benchmark (TP34) elevation as 11464 rather than 14464 which is the correct elevation
Once both topographic surfaces were on the site datum the raw cut volume was obtained by Eaglepoint (Volumes Module) Software utilizing the prismoidal method comparing the two surfaces For reference please see the attached topographic plan which superimposes the October 15 1995 contours (dark lines) over the April 21 1994 contours The volume is based on the intersection of the two surfaces Also it was noted that stock piles of material did exist on site which were not surveyed at the time
The final raw cut volume arrived at by the above methods is 12749 Cubic Yards
In November and December of 1995 the site was resurveyed to locate the area of exposed ledge at the site The results of this survey are shown on the attached topographic worksheet dated November 3 1995 and last revised January 15 1996 The results of the survey indicate the total site area to be 50860 sq ft or 117 acres The total area of exposed ledge surveyed is 19990 sq ft or 46 acres If you have any questions regarding the above call me directly Thank you
Sincerely
John W Myhaver Jr ^_ Field Operations Manager
Enclosure ItorLltr
Route 101 Bedford NH 03110 Phone (603) 472-4488 FAX (603) 472-9747
APPENDIX C
HEALTH AND SAFETY PHASE-OUT REPORT
HEALTH AND SAFETY PHASE-OUT REPORT SALEM ACRES SL-4 AREA
Introduction
During remediation work on SL-4 Health and Safety Monitoring was performed Cashins amp Associates Inc of Reading MA performed the following work as a subcontractor to TFCI
1) Preparation of a site-specific Health and Safety Plan (dated September 1 1995)
2) Provide a Field TechnicianIndustrial Hygienist to serve as Site Safety and Health Officer (SSHO) and to conduct air and noise monitoring
3) Provide a Certified Industrial Hygienist to review Health and Safety and to conduct site specific training (record of training included at end of Appendix C)
4) Collect 8-hour air samples for worker exposure and ambient air at the Barcelona Avenue gate Arrange for analysis of the samples and report results
5) Prepare daily and weekly Health and Safety reports
6) Prepare a Health and Safety Phase-Out Report
In general the following health and safety practices were followed
1) All workers wore hard hats safety glasses work boots gloves and hearing protection as minimum level PPE
2) When working in the exclusion zone workers wore in addition to above tyvek rubber overboots and rubber coated gloves When dust was a potential concern an industrial grade dustmist mask was also worn This level of PPE was considered Level D modified
3) Workers leaving the exclusion zone removed PPE (tyveks gloves boots and masks) in the support zone and either disposed of the items or decontaminated them
4) Workers andor visitors without 40-hour OSHA training were not permitted to enter the exclusion zone
Attached is a report prepared by Cashins amp Associates along with weekly Health and Safety Summary Reports prepared by the Field Hygienist In summary the air monitoring results indicate no levels exceeding the applicable exposure guidelines except one instance
During excavation of contaminated overburden in the northwest comer of the site an area of VOC contaminated soil was encountered Total VOCs levels measured using a PID exceeded the action level established in the Health and Safety Plan The SSHO advised TFCI to upgrade to Level C PPE in order to backfill the excavation in this area TFCI equipment operator upgraded and backfilled the area The SSHO in consultation with the Cashins CIH advised TFCI to avoid work in this area until the contaminants were characterized GEI sampled the material for waste characterization analysis and provided the results to TFCI Based on the results an action level was established by the CIH for the specific contaminants found Further PID measurements indicated levels below the new action level and work was resumed
The noise monitoring indicated that the noise level at the Barcelona Avenue gate was not exceeded Only one instance of excess noise level in the work zone was recorded (10 db(a) above the ambient noise level or 85 db(a)) Workers wore hearing protection in this instance
mdash 07171996 1601 6179444032 CASHIMS S ASSOCIATES PAGE 02
CASHINS amp Associates Inc
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July 17 1996
Mr Jack Enos T Ford Company Inc USTenney Street Georgetown MA 01833
Dear Jack
The Site Safety and Health Officer (SSHO) from Cashing amp Associates Inc performed daily inspections of the SL-4 area Salem Acres Superfund Site between 9595 and 12195 in accordance with the Health amp Safety Plan (HSP) for the site Daily inspection logs were submitted every day No accidentsincidents were reported during the work period
In accordance with the Health amp Safety Plan the SSHO performed daily air and noise monitoring at the site during Ac project Samples were collected for metals (lead beryllium chromium arsenic) and Polynuclear Aromatic Hydrocarbons (PAHs) at the site perimeter and for workers exposure determination Coal Tar Pitch Volatiles (a benzene soluble extractables) were also used to determine the workers exposure to PAH compounds Coal Tar Pitch Volatiles (CTPV) were analyzed using OSHA 58 Method If CTPV levels oq personal samples exceed the site criteria of 02 ragm3 the sample was submitted for PAHs analysis All air samples on the site perimeter were analyzed for PAH compounds
Site monitoring air sample collection and results report were done under the supervision of a Certified Industrial Hygienist
Full shift personal worker exposure samples were collected once a week Ambient air samples were collected at the Barcelona Avenue gate about 20 feet to the west of the site gate to determine if site contaminants were migrating off site The ambient air samples were also collected once a week during the project except on rainy days and days without work with contaminated soil
All air samples were analyzed by the American Industrial Hygiene Association accredited ESA Laboratories Inc using the following methods PAHs - NIOSH 5515 Lead - NIOSH 7082 Beryllium - NIOSH 7102 Chromium - NIOSH 7024 Arsenic - NIOSH 7900 Coal Tar Pitch Volatiles - OSHA 58 All methods used are accepted by the industrial hygiene community for 8-hour exposure assessment EPA methods are usually used for ambient air measurements
CRErORTTFOmiOO
80 Mam Street bull Reading MA 01867 bull Phone- 61 7-944-4060 bull Fax 61 7-944-4082
07171996 1601 6179444032 CASHIMS amp ASSOCIATES PAGE 03
The results of air samples for metals and PAHs are presented in Table No 1
All concentrations of metals and PAHs at the site perimeter (Barcelona Avenue) and active work zones were below the OSHA Permissible Exposure Limits (PEL) and the American Conference of Governmental Industrial Hygicnists Threshold Limit Value (ACGIH TLV) Two personal samples collected on October 19 and October 23rd showed Coal Tar Pitch Volatiles (CTPV) results above OSHA PEL and AIHA TLV limits Both samples were resubmittcd to the lab for further analysis to determine if PAH compounds are present because the CTPV results were above site criteria
The results of the PAH concentrations for the personal sample on Mark Goodwin on October 19 1995 during excavation and washing trucks and for the personal sample on Ron Maker on October 23 1995 during excavating and cleaning rocks by compressed air were below OSHA PEL and ACGIH TLV limits
The SSHO performed noise monitoring according to the HSP at the exclusion zone and at the Barcelona Avenue site perimeter fence A Dupont sound level meter was used for noise monitoring The noise level in the exclusion zone during all operations except one did not exceed the on site criteria of 85 dB(a) During a short time when the air compressor had been used to clean rocks the sound level in the exclusion zone next to the air compressor did exceed 85 dB(a) Ear protection devices were worn by the workers during that operation At no time did the noise level at the Barcelona Avenue site perimeter exceed 10 dB(a) above the ambient noise level or 85 dB(a)
The SSHO performed total dust monitoring on a daily basis during the project at the site perimeter downwind of work location and at the site gate using a Miniram real time dust meter The summary of dust monitoring is presented in Table No 2 Total dust concentrations on site and off site did not exceed site criteria of 1 mgm3 and the action level of 05 nigny1
The summary of air monitoring for Volatile Organic Compounds (VOC) is presented in Table No 3 VOC concentrations in the working area did not exceed the on site criteria of 5 ppm in a breathing zone VOC concentrations on the site perimeter did not exceed real time off site criteria of 2 ppm
Five detail reports with results of air sampling were submitted during the project period
Sincerely Cashins amp Associates Inc
Evelina Vaughan Industrial Hygieflfst
CASHINS amp ASSOCIATES Inc
80 Mam Street bull Reading MA 01867 bull Phone61 7-944-4060 bull Fax 617-944-4082
07171996 1601 6179444082 CASHINS S ASSOCIATES PAGE 04
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CASHINS amp Associates inc
Ifxtuitral Hygltne A fnvironmtnltt Tuning
W3SXLY HBALTH amp SAFETY PLAN COMPLIANCE SUMMARY R3PORT
CLIENT T foyd C o m a n
LOCATION gal era Acres Sx^perfund Site 8L-4 Area
DATES INCLUDED IN SUMMARY
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SUMMARIZED BY FOR CASHINS amp ASSOCIATES INC
55 CAMBRIDGE STREET bull SUITE 201 bull BURLINGTON MA 01803 laquo TEL 61 -273-9080 bull FAX 67-273-9C84
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WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Fprd Company
LOCATION Salen Acres Suoerfund Site SL-4 Area
DATES INCLUDED IN SUMMARY
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Industrial Hygitnf amp CmimnmenUl Tinting
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Compan
LOCATION Salem Acres Superfund Site SL-4 Area
DATES INCLUDED IN SUMMARY
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WEEKLY HEALTH 6 SAFETY PLAN COMPLIANCE SUMMARY REPORT
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LOCATION Salem Acrlaquoa Superfund Site 9L-4 Area
DATES INCLUDED IN SUMMARY
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Industrial Hygiene amp Emironmvntal Testing
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Company
LOCATION Salem Acres Superfund Site SL-4 Area
DATES INCLUDED IN SUMMARY J_
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THE PURPOSE OF THE FOLLOWING STATEMENT IS TO DOCUMENT THE EXISTENCE OF A CONDITION OR CONCERN WHICH CASHINS amp ASSOCIATES INC BELIEVES WARRANTS IMMEDIATE CORRECTIVE ACTION POSSIBLE SOLUTIONS AND OR CORRECTIVE ACTIONS WILL BE INCLUDED IN THIS NOTIFICATION WHEN POSSIBLE THIS NOTIFICATION IS LIMITED TO SITUATIONS THAT REPRESENT EITHER IMMEDIATE DANGER TO LIFE OR HEALTH CONDITIONS OR PREVIOUSLY IDENTIFIED CHRONIC PROBLEMS THAT UNDERMINE OUR ABILITY TO EFFECTIVELY INSURE COMPLIANCE WITH THE REQUIREMENTS OF THE HEALTH AND SAFETY PLAN
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WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
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LOCATION Salem Acres Superfund Site SL-4 Area
DATES INCLUDED IN SUMMARY T
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WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
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LOCATION Salem AcrM Suoerfund Stta 8L-4 Araa
DATES INCLUDED IN SUMMARY
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07151996 18 fO 6179444082 CASHINS S ASSOCIATES PAGE 02
CASHINS amp Associates Inc
WBBKLY HEALTH amp SAFETY FLAK COMPLIANCE SUMMARY REPORT
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LOCATION i Sal am Acrlaquolaquo Suparfund Sita SL-4 Area
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- barcode 14732
- barcodetext SEMS Doc ID 14732
![Page 21: SALEM ACRES SUPERFUND SITE SALEM, MA ...The truck loading pa d consisted of a crushed stone are sea t up along the east sid e o f SL-4 adjacent to the access road A. row of concrete](https://reader036.vdocuments.us/reader036/viewer/2022070114/60729b840fec4e6b4d136a16/html5/thumbnails/21.jpg)
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VIEW OF BOUNDARY BETWEEN SL-4 AND DA-1 LOOKING WEST PRECONSTRUCTION
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(6)
EROSION CONTROLS LOOKING NORTH FROM CORNER OF SL-4SL-5 ADJACENT TO WA-1 PRECONSTRUCTION
(7)
TRUCK LOADING PAD LOOKING NORTHWEST FROM SUPPORT ZONE
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(8)
DECONTAMINATION PAD LOOKING NORTHWEST FROM SUPPORT ZONE
(9)
EXCAVATION OF FLY ASH LOOKING NORTHWEST FROM CRZ NOTE WATER FOR DUST CONTROL
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(10)
VIEW LOOKING WEST AFTER REMOVAL OF FLY ASH NOTE WA-1 BEYOND EROSION CONTROLS
(11)
EXCAVATION OF CONTAMINATED OVERBURDEN LOOKING SOUTH FROM DA-1 BOUNDARY
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(12)
VIEW OF RESTORED SITE LOOKING WEST TOWARD WA-1
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VIEW OF RESTORED SITE LOOKING NORTH TOWARD DA-1 ALONG ACCESS ROAD
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(15)
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VIEW OF RESTORED SITE ON DA-1 SJDE OF FENCE - LOOKING ST
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(18)
VIEW OF RESTORED SITE ON DA-1 SIDE OF FENCE - LOOKING WEST SL-4 ON RIGHT
APPENDIX A
ANALYTICAL RESULTS FOR
PONDED WATER
110795 1638 copy617 890 3883 TMA-WALTHAM ] 002007
PRELIMINARY REPORT UNAUDITED RESULTS
Thenno Analytical 300 Second Avenue PO Box 521 Waltham HA 02254
Attn Client Services Phone (617) 890-7200
Cashins amp Associates Order S5-11-034 55 Cambridge Street Date 110795 1522 Burlington HA 01803 Work ID Salem Acres Water
Date Received 110295 Attn Bob Cashins Date Completed
Purchase Order NA Invoice Number Client Code CASHINS
SAMPLE IDENTIFICATION
Sample Sample Number Description 01 11019S-924-01A
Sample Number 04
Sample Description
110195-9Z4-01D 02 110195-924-01B 05 110195-924-01E 03 110195-924-01C
Certified By
110795 1638 copy617 890 3883 TMA-WALTHAM 003007
PRELIMINARY REPORT UNAUDITED RESULTS
Order f S5-11-034 Thermo Analytical Page 2 110795 1522 TEST RESULTS BY SAHPLE
Test Description Volatile Organics- Aqueous Method EPA_8240 Test Code Collected 110195 02-00 Category WATER
DATE INJECTED 110695 DILUTION FACTOR 100 All results reported 1n ugL
COMPOUND RESULT DET LIMIT COMPOUND RESULT
Chloromethane U 10 Broroodi chl oromethane U Vinyl Chloride U 10 2-Chloroethyl Vinyl Ether U
Bromxnethane U 10 4-dethyl -2-pentanone U Chloroethane U 10 c1 3-1 3-Di chl oropropene U
Trichlorofluoronwthane U 50 Tol uene U Acetone 17 10 trans-1 3-Di chl oropropene LI
11-Oichloroethene U 50 11 2-Tri chl oroethane J Carbon Dlsulfide U 50 2-Hexanone U
Methyl ene Chloride U 50 Tetrachl oroethene U 12-Oichloroethene (total) U 50 D1 bromochl oromethane U
11-01 Chloroethane U 50 Chlorobenzene U Vinyl Acetate U 10 Ethyl benzene U
2-Butanone U 10 in and p-Xylene U Chloroform U 50 o-Xylene U
111-Tri Chloroethane U 50 Styrene U Carbon Tetrachlortde U 50 Broraoform U
Benzene U 50 112 2-Tat rachl oroethane U 12-01 Chloroethane U 50 1 3-01 chl orobenzene U
Trichloroethene U 50 I 4-Di chl orobenzene U 12-Dichloropropane U 50 12-01 chl orobenzene U
SURROGATE STANDARDS RESULT LEVEL X RECOVERY
12-Dichloroethane-D4 52 50 104 Toluene-08 47 50 94
l-Bromo-4-fluorobenzene 56 50 112
NOTES AND DEFINITIONS FOR THIS REPORT U =bull Undetected at stated detection limit
VOAJI
OET LIMIT
50 50
10 50 50 50 50 10
5 0 50 5 0 5 0 50 50 50 50 50 50 50 50
110795 1639 copy617 890 3883 TMA-WALTHAM copy004007
PRELIMINARY REPORT UNAUDITED RESULTS
Order t S5-11-034 Thermo Analytical Page 4 110795 1522 TEST RESULTS BY SAMPLE
ianple Description 110195-924-010 Lab No 04A Test Description RCRA Metals 1n Water Method SW846 Test Code
Collected 110195 0200 Category WATER
METAL RESULT DETECTION LIMIT METAL RESULT DETECTION LIMIT
Ag Silver U 10 As Arsenic 870 50
Ba Bar inn B69 10 Pb Lead U 50
Cd Cadmium U 50 Se Sel en1 um Z15 50
Cr Chromi um U 20 Hg Mercury U 020
NOTES AND DEFINITIONS FOR THIS REPORT All results reported in ugL U gt Undetected at stated detection limit
110795 1640 Q617 890 3883 TMA-WALTHAM 0005007
PRELIMINARY REPORT UNAUDITED RESULTS
Order S5-11-034 Thermo Analytical Page 5 110795 1522 REGULAR TEST RESULTS BY TEST
Chemical Oxygen Demand Mlnimun Maximum Method EPA600 4101
Sap Sample Description Result Units Limit Prepared Analyzed By 05A 110195-924-01E 64 bullgL 50 110395 110395 JD
Petroleum Hydrocarbons-H20 Minimum Maximum Method EPA600 4181
Samp Sample Description Result Units Limit Prepared Analyzed By 01A 110195-924-01A 108 mgL 050 110395 110395 JO
110795 1640 reg617 890 3883 TMA-WALTHAM copy006007
PRELIMINARY REPORT UNAUDITED RESULTS
Order I S5-11-034 Therm Analytical Page 6 110795 1522 TEST METHODOLOGIES
USEPA Test Methods for Evaluating Solid Wastes (SUS46 Third Edition) Method 7470 - Preparation of water for Mercury analysis
USEPA Test Methods for Evaluating Solid Vastes (SW846 Third Edition) Method 3010 - Add digestion of aqueous samples and extracts for total metals for analysis by Flame Atomic Absorption Spectroscopy or Inductively Coupled Plasma Spectroscopy
USEPA Test Methods for Evaluating Solid Vastes (SWB46 Third Edition Method 8270 mdash Gas ChroroatographyMass Spectrometry for PAHs
Volatile Organics in Water - Hazardous Substance List
SV846 Method 8240 - Modified
Test Methods for Evaluating Solid Waste SU-846 US EPA Office of Solid Waste and Emergency Response Washington 3rd Edition
Aqueous sanples are analyzed in accordance with Method 8240 using a purge and trap technique followed by 64s ChromatographyMass Spectroscopy
Quality assurance procedures for GCMS Include daily tuning and calibration of the mass spectrometer and the use of surrogate standards in each sample to monitor method performance Quantitatton is performed by the Internal standard method Analysis of blanks duplicate samples and standards are run frequently as further quality assurance procedures
USEPA Test Methods for Evaluating Solid Wastes (SW846 Third Edition) Method 3S10 mdash Separatory Funnel Liquid-Liquid Extraction
EPA-6004-79-020 - Chemical Oxygen Demand - Titrimetric Mid-Level Method 4101
EPA6004-79-020 - Petroleum Hydrocarbons 1n Water Total Recoverable Method 4181 (Spectrophotometric Infrared)
110795 1641 copy617 890 3883 TMA-WALTHAM copy007007
APPENDIX B
QUANTITY SURVEY DOCUMENTATION
TFMORAN INC Surveying - Engineering - Land Planning SoilsWetlands Mapping - Landscape Architecture
January 15 1996
Mr Jack Enos Vice President TFord Company Inc 118 Tenney Street Georgetown MA 01833
RE Survey Results - Salem Acres - SL4 Area Salem Massachusetts
Dear Jack
This letter amends the letter of December 13 1995 per our review last week
TFMoran Inc performed topographic surveys at the Salem Acres site on April 21 1994 for GEI Consultants prior to removal of material and for TFord Company on October 18 1995 after the removal of material The survey data from the original survey in 1994 was adjusted thirty feet higher to correct for a datum difference from current site datum This was due to the original reporting of the Site Benchmark (TP34) elevation as 11464 rather than 14464 which is the correct elevation
Once both topographic surfaces were on the site datum the raw cut volume was obtained by Eaglepoint (Volumes Module) Software utilizing the prismoidal method comparing the two surfaces For reference please see the attached topographic plan which superimposes the October 15 1995 contours (dark lines) over the April 21 1994 contours The volume is based on the intersection of the two surfaces Also it was noted that stock piles of material did exist on site which were not surveyed at the time
The final raw cut volume arrived at by the above methods is 12749 Cubic Yards
In November and December of 1995 the site was resurveyed to locate the area of exposed ledge at the site The results of this survey are shown on the attached topographic worksheet dated November 3 1995 and last revised January 15 1996 The results of the survey indicate the total site area to be 50860 sq ft or 117 acres The total area of exposed ledge surveyed is 19990 sq ft or 46 acres If you have any questions regarding the above call me directly Thank you
Sincerely
John W Myhaver Jr ^_ Field Operations Manager
Enclosure ItorLltr
Route 101 Bedford NH 03110 Phone (603) 472-4488 FAX (603) 472-9747
APPENDIX C
HEALTH AND SAFETY PHASE-OUT REPORT
HEALTH AND SAFETY PHASE-OUT REPORT SALEM ACRES SL-4 AREA
Introduction
During remediation work on SL-4 Health and Safety Monitoring was performed Cashins amp Associates Inc of Reading MA performed the following work as a subcontractor to TFCI
1) Preparation of a site-specific Health and Safety Plan (dated September 1 1995)
2) Provide a Field TechnicianIndustrial Hygienist to serve as Site Safety and Health Officer (SSHO) and to conduct air and noise monitoring
3) Provide a Certified Industrial Hygienist to review Health and Safety and to conduct site specific training (record of training included at end of Appendix C)
4) Collect 8-hour air samples for worker exposure and ambient air at the Barcelona Avenue gate Arrange for analysis of the samples and report results
5) Prepare daily and weekly Health and Safety reports
6) Prepare a Health and Safety Phase-Out Report
In general the following health and safety practices were followed
1) All workers wore hard hats safety glasses work boots gloves and hearing protection as minimum level PPE
2) When working in the exclusion zone workers wore in addition to above tyvek rubber overboots and rubber coated gloves When dust was a potential concern an industrial grade dustmist mask was also worn This level of PPE was considered Level D modified
3) Workers leaving the exclusion zone removed PPE (tyveks gloves boots and masks) in the support zone and either disposed of the items or decontaminated them
4) Workers andor visitors without 40-hour OSHA training were not permitted to enter the exclusion zone
Attached is a report prepared by Cashins amp Associates along with weekly Health and Safety Summary Reports prepared by the Field Hygienist In summary the air monitoring results indicate no levels exceeding the applicable exposure guidelines except one instance
During excavation of contaminated overburden in the northwest comer of the site an area of VOC contaminated soil was encountered Total VOCs levels measured using a PID exceeded the action level established in the Health and Safety Plan The SSHO advised TFCI to upgrade to Level C PPE in order to backfill the excavation in this area TFCI equipment operator upgraded and backfilled the area The SSHO in consultation with the Cashins CIH advised TFCI to avoid work in this area until the contaminants were characterized GEI sampled the material for waste characterization analysis and provided the results to TFCI Based on the results an action level was established by the CIH for the specific contaminants found Further PID measurements indicated levels below the new action level and work was resumed
The noise monitoring indicated that the noise level at the Barcelona Avenue gate was not exceeded Only one instance of excess noise level in the work zone was recorded (10 db(a) above the ambient noise level or 85 db(a)) Workers wore hearing protection in this instance
mdash 07171996 1601 6179444032 CASHIMS S ASSOCIATES PAGE 02
CASHINS amp Associates Inc
ItxhalrM Hy-gifnr A Invtronmtnltl Tttling
July 17 1996
Mr Jack Enos T Ford Company Inc USTenney Street Georgetown MA 01833
Dear Jack
The Site Safety and Health Officer (SSHO) from Cashing amp Associates Inc performed daily inspections of the SL-4 area Salem Acres Superfund Site between 9595 and 12195 in accordance with the Health amp Safety Plan (HSP) for the site Daily inspection logs were submitted every day No accidentsincidents were reported during the work period
In accordance with the Health amp Safety Plan the SSHO performed daily air and noise monitoring at the site during Ac project Samples were collected for metals (lead beryllium chromium arsenic) and Polynuclear Aromatic Hydrocarbons (PAHs) at the site perimeter and for workers exposure determination Coal Tar Pitch Volatiles (a benzene soluble extractables) were also used to determine the workers exposure to PAH compounds Coal Tar Pitch Volatiles (CTPV) were analyzed using OSHA 58 Method If CTPV levels oq personal samples exceed the site criteria of 02 ragm3 the sample was submitted for PAHs analysis All air samples on the site perimeter were analyzed for PAH compounds
Site monitoring air sample collection and results report were done under the supervision of a Certified Industrial Hygienist
Full shift personal worker exposure samples were collected once a week Ambient air samples were collected at the Barcelona Avenue gate about 20 feet to the west of the site gate to determine if site contaminants were migrating off site The ambient air samples were also collected once a week during the project except on rainy days and days without work with contaminated soil
All air samples were analyzed by the American Industrial Hygiene Association accredited ESA Laboratories Inc using the following methods PAHs - NIOSH 5515 Lead - NIOSH 7082 Beryllium - NIOSH 7102 Chromium - NIOSH 7024 Arsenic - NIOSH 7900 Coal Tar Pitch Volatiles - OSHA 58 All methods used are accepted by the industrial hygiene community for 8-hour exposure assessment EPA methods are usually used for ambient air measurements
CRErORTTFOmiOO
80 Mam Street bull Reading MA 01867 bull Phone- 61 7-944-4060 bull Fax 61 7-944-4082
07171996 1601 6179444032 CASHIMS amp ASSOCIATES PAGE 03
The results of air samples for metals and PAHs are presented in Table No 1
All concentrations of metals and PAHs at the site perimeter (Barcelona Avenue) and active work zones were below the OSHA Permissible Exposure Limits (PEL) and the American Conference of Governmental Industrial Hygicnists Threshold Limit Value (ACGIH TLV) Two personal samples collected on October 19 and October 23rd showed Coal Tar Pitch Volatiles (CTPV) results above OSHA PEL and AIHA TLV limits Both samples were resubmittcd to the lab for further analysis to determine if PAH compounds are present because the CTPV results were above site criteria
The results of the PAH concentrations for the personal sample on Mark Goodwin on October 19 1995 during excavation and washing trucks and for the personal sample on Ron Maker on October 23 1995 during excavating and cleaning rocks by compressed air were below OSHA PEL and ACGIH TLV limits
The SSHO performed noise monitoring according to the HSP at the exclusion zone and at the Barcelona Avenue site perimeter fence A Dupont sound level meter was used for noise monitoring The noise level in the exclusion zone during all operations except one did not exceed the on site criteria of 85 dB(a) During a short time when the air compressor had been used to clean rocks the sound level in the exclusion zone next to the air compressor did exceed 85 dB(a) Ear protection devices were worn by the workers during that operation At no time did the noise level at the Barcelona Avenue site perimeter exceed 10 dB(a) above the ambient noise level or 85 dB(a)
The SSHO performed total dust monitoring on a daily basis during the project at the site perimeter downwind of work location and at the site gate using a Miniram real time dust meter The summary of dust monitoring is presented in Table No 2 Total dust concentrations on site and off site did not exceed site criteria of 1 mgm3 and the action level of 05 nigny1
The summary of air monitoring for Volatile Organic Compounds (VOC) is presented in Table No 3 VOC concentrations in the working area did not exceed the on site criteria of 5 ppm in a breathing zone VOC concentrations on the site perimeter did not exceed real time off site criteria of 2 ppm
Five detail reports with results of air sampling were submitted during the project period
Sincerely Cashins amp Associates Inc
Evelina Vaughan Industrial Hygieflfst
CASHINS amp ASSOCIATES Inc
80 Mam Street bull Reading MA 01867 bull Phone61 7-944-4060 bull Fax 617-944-4082
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CASHINS amp Associates Inc
Industrial Hygiene amp Environmental Testing
SITE SPECIFIC amp HAZARD COMMUNICATIONS TRAINING SIGN-IN SHEET
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OSHINSamp Associates Inc
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89111995 1023 6172733(384 CASHINS ASSOCIATES PAGE 01
CASHINS amp Associates inc
Ifxtuitral Hygltne A fnvironmtnltt Tuning
W3SXLY HBALTH amp SAFETY PLAN COMPLIANCE SUMMARY R3PORT
CLIENT T foyd C o m a n
LOCATION gal era Acres Sx^perfund Site 8L-4 Area
DATES INCLUDED IN SUMMARY
toe
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SUMMARIZED BY FOR CASHINS amp ASSOCIATES INC
55 CAMBRIDGE STREET bull SUITE 201 bull BURLINGTON MA 01803 laquo TEL 61 -273-9080 bull FAX 67-273-9C84
09111995 1023 6172739084 CASHINS ASSOCIATES PAGE 01
CASHINSamp Associates Inc
Induttrml Hygttnr t Emtroomtnttl Ttstinf
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Fprd Company
LOCATION Salen Acres Suoerfund Site SL-4 Area
DATES INCLUDED IN SUMMARY
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55 CAMBRIDGE STREET bull SUITE 201 bull BURLINGTON MA 01803 raquo- TEL 6J 7-273-9080 bull FAX 617-273-9084
CASHINS amp Associates Inc
Industrial Hygitnf amp CmimnmenUl Tinting
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Compan
LOCATION Salem Acres Superfund Site SL-4 Area
DATES INCLUDED IN SUMMARY
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LOCATION Salam Aerag SL-4
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WEEKLY HEALTH 6 SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Fortjl Cqjapany
LOCATION Salem Acrlaquoa Superfund Site 9L-4 Area
DATES INCLUDED IN SUMMARY
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Industrial Hygiene amp Emironmvntal Testing
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Company
LOCATION Salem Acres Superfund Site SL-4 Area
DATES INCLUDED IN SUMMARY J_
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SERIOUS HAZARD NOTIFICATION
ISSUED TO REPRESENTING
ISSUED BY REPRESENTING CASHINS S ASSOCIATES INcT DAY DATE ISSUED O04Xmdash 1 bull-bullmdashbull f P^JT
PROJECT NAME_ SITE LOCATION
THE PURPOSE OF THE FOLLOWING STATEMENT IS TO DOCUMENT THE EXISTENCE OF A CONDITION OR CONCERN WHICH CASHINS amp ASSOCIATES INC BELIEVES WARRANTS IMMEDIATE CORRECTIVE ACTION POSSIBLE SOLUTIONS AND OR CORRECTIVE ACTIONS WILL BE INCLUDED IN THIS NOTIFICATION WHEN POSSIBLE THIS NOTIFICATION IS LIMITED TO SITUATIONS THAT REPRESENT EITHER IMMEDIATE DANGER TO LIFE OR HEALTH CONDITIONS OR PREVIOUSLY IDENTIFIED CHRONIC PROBLEMS THAT UNDERMINE OUR ABILITY TO EFFECTIVELY INSURE COMPLIANCE WITH THE REQUIREMENTS OF THE HEALTH AND SAFETY PLAN
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Industrial Hygirne amp Cmimnmtntal Testing
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Company
LOCATION Salem Acres Superfund Site SL-4 Area
DATES INCLUDED IN SUMMARY T
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WEEKLY HEALTH amp SA7STT PLAN COMPLIANCE SUMMARY REPORT
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LOCATION Sa^am Acras Super fund 5 jte SL-4 Area
DATES INCLUDED IN SUMMARY bull
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LOCATION Salem Acraa Suoerfund Sita 5L-4
DATES INCLUDED IN SUMMARY bull
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LOCATION t Salam Acraa Suoarfund Site SL-4 Arlaquoa
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WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Company T
LOCATION Salem AcrM Suoerfund Stta 8L-4 Araa
DATES INCLUDED IN SUMMARY
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CASHINS amp Associates Inc
WBBKLY HEALTH amp SAFETY FLAK COMPLIANCE SUMMARY REPORT
CLIENT T Ford Compapv
LOCATION i Sal am Acrlaquolaquo Suparfund Sita SL-4 Area
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- barcode 14732
- barcodetext SEMS Doc ID 14732
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(5)
VIEW OF BOUNDARY BETWEEN SL-4 AND DA-1 LOOKING WEST PRECONSTRUCTION
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(6)
EROSION CONTROLS LOOKING NORTH FROM CORNER OF SL-4SL-5 ADJACENT TO WA-1 PRECONSTRUCTION
(7)
TRUCK LOADING PAD LOOKING NORTHWEST FROM SUPPORT ZONE
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(8)
DECONTAMINATION PAD LOOKING NORTHWEST FROM SUPPORT ZONE
(9)
EXCAVATION OF FLY ASH LOOKING NORTHWEST FROM CRZ NOTE WATER FOR DUST CONTROL
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(10)
VIEW LOOKING WEST AFTER REMOVAL OF FLY ASH NOTE WA-1 BEYOND EROSION CONTROLS
(11)
EXCAVATION OF CONTAMINATED OVERBURDEN LOOKING SOUTH FROM DA-1 BOUNDARY
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(12)
VIEW OF RESTORED SITE LOOKING WEST TOWARD WA-1
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ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(15)
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VIEW OF RESTORED SITE ON DA-1 SJDE OF FENCE - LOOKING ST
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(18)
VIEW OF RESTORED SITE ON DA-1 SIDE OF FENCE - LOOKING WEST SL-4 ON RIGHT
APPENDIX A
ANALYTICAL RESULTS FOR
PONDED WATER
110795 1638 copy617 890 3883 TMA-WALTHAM ] 002007
PRELIMINARY REPORT UNAUDITED RESULTS
Thenno Analytical 300 Second Avenue PO Box 521 Waltham HA 02254
Attn Client Services Phone (617) 890-7200
Cashins amp Associates Order S5-11-034 55 Cambridge Street Date 110795 1522 Burlington HA 01803 Work ID Salem Acres Water
Date Received 110295 Attn Bob Cashins Date Completed
Purchase Order NA Invoice Number Client Code CASHINS
SAMPLE IDENTIFICATION
Sample Sample Number Description 01 11019S-924-01A
Sample Number 04
Sample Description
110195-9Z4-01D 02 110195-924-01B 05 110195-924-01E 03 110195-924-01C
Certified By
110795 1638 copy617 890 3883 TMA-WALTHAM 003007
PRELIMINARY REPORT UNAUDITED RESULTS
Order f S5-11-034 Thermo Analytical Page 2 110795 1522 TEST RESULTS BY SAHPLE
Test Description Volatile Organics- Aqueous Method EPA_8240 Test Code Collected 110195 02-00 Category WATER
DATE INJECTED 110695 DILUTION FACTOR 100 All results reported 1n ugL
COMPOUND RESULT DET LIMIT COMPOUND RESULT
Chloromethane U 10 Broroodi chl oromethane U Vinyl Chloride U 10 2-Chloroethyl Vinyl Ether U
Bromxnethane U 10 4-dethyl -2-pentanone U Chloroethane U 10 c1 3-1 3-Di chl oropropene U
Trichlorofluoronwthane U 50 Tol uene U Acetone 17 10 trans-1 3-Di chl oropropene LI
11-Oichloroethene U 50 11 2-Tri chl oroethane J Carbon Dlsulfide U 50 2-Hexanone U
Methyl ene Chloride U 50 Tetrachl oroethene U 12-Oichloroethene (total) U 50 D1 bromochl oromethane U
11-01 Chloroethane U 50 Chlorobenzene U Vinyl Acetate U 10 Ethyl benzene U
2-Butanone U 10 in and p-Xylene U Chloroform U 50 o-Xylene U
111-Tri Chloroethane U 50 Styrene U Carbon Tetrachlortde U 50 Broraoform U
Benzene U 50 112 2-Tat rachl oroethane U 12-01 Chloroethane U 50 1 3-01 chl orobenzene U
Trichloroethene U 50 I 4-Di chl orobenzene U 12-Dichloropropane U 50 12-01 chl orobenzene U
SURROGATE STANDARDS RESULT LEVEL X RECOVERY
12-Dichloroethane-D4 52 50 104 Toluene-08 47 50 94
l-Bromo-4-fluorobenzene 56 50 112
NOTES AND DEFINITIONS FOR THIS REPORT U =bull Undetected at stated detection limit
VOAJI
OET LIMIT
50 50
10 50 50 50 50 10
5 0 50 5 0 5 0 50 50 50 50 50 50 50 50
110795 1639 copy617 890 3883 TMA-WALTHAM copy004007
PRELIMINARY REPORT UNAUDITED RESULTS
Order t S5-11-034 Thermo Analytical Page 4 110795 1522 TEST RESULTS BY SAMPLE
ianple Description 110195-924-010 Lab No 04A Test Description RCRA Metals 1n Water Method SW846 Test Code
Collected 110195 0200 Category WATER
METAL RESULT DETECTION LIMIT METAL RESULT DETECTION LIMIT
Ag Silver U 10 As Arsenic 870 50
Ba Bar inn B69 10 Pb Lead U 50
Cd Cadmium U 50 Se Sel en1 um Z15 50
Cr Chromi um U 20 Hg Mercury U 020
NOTES AND DEFINITIONS FOR THIS REPORT All results reported in ugL U gt Undetected at stated detection limit
110795 1640 Q617 890 3883 TMA-WALTHAM 0005007
PRELIMINARY REPORT UNAUDITED RESULTS
Order S5-11-034 Thermo Analytical Page 5 110795 1522 REGULAR TEST RESULTS BY TEST
Chemical Oxygen Demand Mlnimun Maximum Method EPA600 4101
Sap Sample Description Result Units Limit Prepared Analyzed By 05A 110195-924-01E 64 bullgL 50 110395 110395 JD
Petroleum Hydrocarbons-H20 Minimum Maximum Method EPA600 4181
Samp Sample Description Result Units Limit Prepared Analyzed By 01A 110195-924-01A 108 mgL 050 110395 110395 JO
110795 1640 reg617 890 3883 TMA-WALTHAM copy006007
PRELIMINARY REPORT UNAUDITED RESULTS
Order I S5-11-034 Therm Analytical Page 6 110795 1522 TEST METHODOLOGIES
USEPA Test Methods for Evaluating Solid Wastes (SUS46 Third Edition) Method 7470 - Preparation of water for Mercury analysis
USEPA Test Methods for Evaluating Solid Vastes (SW846 Third Edition) Method 3010 - Add digestion of aqueous samples and extracts for total metals for analysis by Flame Atomic Absorption Spectroscopy or Inductively Coupled Plasma Spectroscopy
USEPA Test Methods for Evaluating Solid Vastes (SWB46 Third Edition Method 8270 mdash Gas ChroroatographyMass Spectrometry for PAHs
Volatile Organics in Water - Hazardous Substance List
SV846 Method 8240 - Modified
Test Methods for Evaluating Solid Waste SU-846 US EPA Office of Solid Waste and Emergency Response Washington 3rd Edition
Aqueous sanples are analyzed in accordance with Method 8240 using a purge and trap technique followed by 64s ChromatographyMass Spectroscopy
Quality assurance procedures for GCMS Include daily tuning and calibration of the mass spectrometer and the use of surrogate standards in each sample to monitor method performance Quantitatton is performed by the Internal standard method Analysis of blanks duplicate samples and standards are run frequently as further quality assurance procedures
USEPA Test Methods for Evaluating Solid Wastes (SW846 Third Edition) Method 3S10 mdash Separatory Funnel Liquid-Liquid Extraction
EPA-6004-79-020 - Chemical Oxygen Demand - Titrimetric Mid-Level Method 4101
EPA6004-79-020 - Petroleum Hydrocarbons 1n Water Total Recoverable Method 4181 (Spectrophotometric Infrared)
110795 1641 copy617 890 3883 TMA-WALTHAM copy007007
APPENDIX B
QUANTITY SURVEY DOCUMENTATION
TFMORAN INC Surveying - Engineering - Land Planning SoilsWetlands Mapping - Landscape Architecture
January 15 1996
Mr Jack Enos Vice President TFord Company Inc 118 Tenney Street Georgetown MA 01833
RE Survey Results - Salem Acres - SL4 Area Salem Massachusetts
Dear Jack
This letter amends the letter of December 13 1995 per our review last week
TFMoran Inc performed topographic surveys at the Salem Acres site on April 21 1994 for GEI Consultants prior to removal of material and for TFord Company on October 18 1995 after the removal of material The survey data from the original survey in 1994 was adjusted thirty feet higher to correct for a datum difference from current site datum This was due to the original reporting of the Site Benchmark (TP34) elevation as 11464 rather than 14464 which is the correct elevation
Once both topographic surfaces were on the site datum the raw cut volume was obtained by Eaglepoint (Volumes Module) Software utilizing the prismoidal method comparing the two surfaces For reference please see the attached topographic plan which superimposes the October 15 1995 contours (dark lines) over the April 21 1994 contours The volume is based on the intersection of the two surfaces Also it was noted that stock piles of material did exist on site which were not surveyed at the time
The final raw cut volume arrived at by the above methods is 12749 Cubic Yards
In November and December of 1995 the site was resurveyed to locate the area of exposed ledge at the site The results of this survey are shown on the attached topographic worksheet dated November 3 1995 and last revised January 15 1996 The results of the survey indicate the total site area to be 50860 sq ft or 117 acres The total area of exposed ledge surveyed is 19990 sq ft or 46 acres If you have any questions regarding the above call me directly Thank you
Sincerely
John W Myhaver Jr ^_ Field Operations Manager
Enclosure ItorLltr
Route 101 Bedford NH 03110 Phone (603) 472-4488 FAX (603) 472-9747
APPENDIX C
HEALTH AND SAFETY PHASE-OUT REPORT
HEALTH AND SAFETY PHASE-OUT REPORT SALEM ACRES SL-4 AREA
Introduction
During remediation work on SL-4 Health and Safety Monitoring was performed Cashins amp Associates Inc of Reading MA performed the following work as a subcontractor to TFCI
1) Preparation of a site-specific Health and Safety Plan (dated September 1 1995)
2) Provide a Field TechnicianIndustrial Hygienist to serve as Site Safety and Health Officer (SSHO) and to conduct air and noise monitoring
3) Provide a Certified Industrial Hygienist to review Health and Safety and to conduct site specific training (record of training included at end of Appendix C)
4) Collect 8-hour air samples for worker exposure and ambient air at the Barcelona Avenue gate Arrange for analysis of the samples and report results
5) Prepare daily and weekly Health and Safety reports
6) Prepare a Health and Safety Phase-Out Report
In general the following health and safety practices were followed
1) All workers wore hard hats safety glasses work boots gloves and hearing protection as minimum level PPE
2) When working in the exclusion zone workers wore in addition to above tyvek rubber overboots and rubber coated gloves When dust was a potential concern an industrial grade dustmist mask was also worn This level of PPE was considered Level D modified
3) Workers leaving the exclusion zone removed PPE (tyveks gloves boots and masks) in the support zone and either disposed of the items or decontaminated them
4) Workers andor visitors without 40-hour OSHA training were not permitted to enter the exclusion zone
Attached is a report prepared by Cashins amp Associates along with weekly Health and Safety Summary Reports prepared by the Field Hygienist In summary the air monitoring results indicate no levels exceeding the applicable exposure guidelines except one instance
During excavation of contaminated overburden in the northwest comer of the site an area of VOC contaminated soil was encountered Total VOCs levels measured using a PID exceeded the action level established in the Health and Safety Plan The SSHO advised TFCI to upgrade to Level C PPE in order to backfill the excavation in this area TFCI equipment operator upgraded and backfilled the area The SSHO in consultation with the Cashins CIH advised TFCI to avoid work in this area until the contaminants were characterized GEI sampled the material for waste characterization analysis and provided the results to TFCI Based on the results an action level was established by the CIH for the specific contaminants found Further PID measurements indicated levels below the new action level and work was resumed
The noise monitoring indicated that the noise level at the Barcelona Avenue gate was not exceeded Only one instance of excess noise level in the work zone was recorded (10 db(a) above the ambient noise level or 85 db(a)) Workers wore hearing protection in this instance
mdash 07171996 1601 6179444032 CASHIMS S ASSOCIATES PAGE 02
CASHINS amp Associates Inc
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July 17 1996
Mr Jack Enos T Ford Company Inc USTenney Street Georgetown MA 01833
Dear Jack
The Site Safety and Health Officer (SSHO) from Cashing amp Associates Inc performed daily inspections of the SL-4 area Salem Acres Superfund Site between 9595 and 12195 in accordance with the Health amp Safety Plan (HSP) for the site Daily inspection logs were submitted every day No accidentsincidents were reported during the work period
In accordance with the Health amp Safety Plan the SSHO performed daily air and noise monitoring at the site during Ac project Samples were collected for metals (lead beryllium chromium arsenic) and Polynuclear Aromatic Hydrocarbons (PAHs) at the site perimeter and for workers exposure determination Coal Tar Pitch Volatiles (a benzene soluble extractables) were also used to determine the workers exposure to PAH compounds Coal Tar Pitch Volatiles (CTPV) were analyzed using OSHA 58 Method If CTPV levels oq personal samples exceed the site criteria of 02 ragm3 the sample was submitted for PAHs analysis All air samples on the site perimeter were analyzed for PAH compounds
Site monitoring air sample collection and results report were done under the supervision of a Certified Industrial Hygienist
Full shift personal worker exposure samples were collected once a week Ambient air samples were collected at the Barcelona Avenue gate about 20 feet to the west of the site gate to determine if site contaminants were migrating off site The ambient air samples were also collected once a week during the project except on rainy days and days without work with contaminated soil
All air samples were analyzed by the American Industrial Hygiene Association accredited ESA Laboratories Inc using the following methods PAHs - NIOSH 5515 Lead - NIOSH 7082 Beryllium - NIOSH 7102 Chromium - NIOSH 7024 Arsenic - NIOSH 7900 Coal Tar Pitch Volatiles - OSHA 58 All methods used are accepted by the industrial hygiene community for 8-hour exposure assessment EPA methods are usually used for ambient air measurements
CRErORTTFOmiOO
80 Mam Street bull Reading MA 01867 bull Phone- 61 7-944-4060 bull Fax 61 7-944-4082
07171996 1601 6179444032 CASHIMS amp ASSOCIATES PAGE 03
The results of air samples for metals and PAHs are presented in Table No 1
All concentrations of metals and PAHs at the site perimeter (Barcelona Avenue) and active work zones were below the OSHA Permissible Exposure Limits (PEL) and the American Conference of Governmental Industrial Hygicnists Threshold Limit Value (ACGIH TLV) Two personal samples collected on October 19 and October 23rd showed Coal Tar Pitch Volatiles (CTPV) results above OSHA PEL and AIHA TLV limits Both samples were resubmittcd to the lab for further analysis to determine if PAH compounds are present because the CTPV results were above site criteria
The results of the PAH concentrations for the personal sample on Mark Goodwin on October 19 1995 during excavation and washing trucks and for the personal sample on Ron Maker on October 23 1995 during excavating and cleaning rocks by compressed air were below OSHA PEL and ACGIH TLV limits
The SSHO performed noise monitoring according to the HSP at the exclusion zone and at the Barcelona Avenue site perimeter fence A Dupont sound level meter was used for noise monitoring The noise level in the exclusion zone during all operations except one did not exceed the on site criteria of 85 dB(a) During a short time when the air compressor had been used to clean rocks the sound level in the exclusion zone next to the air compressor did exceed 85 dB(a) Ear protection devices were worn by the workers during that operation At no time did the noise level at the Barcelona Avenue site perimeter exceed 10 dB(a) above the ambient noise level or 85 dB(a)
The SSHO performed total dust monitoring on a daily basis during the project at the site perimeter downwind of work location and at the site gate using a Miniram real time dust meter The summary of dust monitoring is presented in Table No 2 Total dust concentrations on site and off site did not exceed site criteria of 1 mgm3 and the action level of 05 nigny1
The summary of air monitoring for Volatile Organic Compounds (VOC) is presented in Table No 3 VOC concentrations in the working area did not exceed the on site criteria of 5 ppm in a breathing zone VOC concentrations on the site perimeter did not exceed real time off site criteria of 2 ppm
Five detail reports with results of air sampling were submitted during the project period
Sincerely Cashins amp Associates Inc
Evelina Vaughan Industrial Hygieflfst
CASHINS amp ASSOCIATES Inc
80 Mam Street bull Reading MA 01867 bull Phone61 7-944-4060 bull Fax 617-944-4082
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SITE SPECIFIC amp HAZARD COMMUNICATIONS TRAINING SIGN-IN SHEET
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CASHINS amp Associates inc
Ifxtuitral Hygltne A fnvironmtnltt Tuning
W3SXLY HBALTH amp SAFETY PLAN COMPLIANCE SUMMARY R3PORT
CLIENT T foyd C o m a n
LOCATION gal era Acres Sx^perfund Site 8L-4 Area
DATES INCLUDED IN SUMMARY
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CASHINSamp Associates Inc
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WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
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LOCATION Salen Acres Suoerfund Site SL-4 Area
DATES INCLUDED IN SUMMARY
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WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
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LOCATION Salem Acres Superfund Site SL-4 Area
DATES INCLUDED IN SUMMARY
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CASHINSamp Associates Inc
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WEEKLY HEALTH 6 SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Fortjl Cqjapany
LOCATION Salem Acrlaquoa Superfund Site 9L-4 Area
DATES INCLUDED IN SUMMARY
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CLIENT T Ford Company
LOCATION Salem Acres Superfund Site SL-4 Area
DATES INCLUDED IN SUMMARY J_
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ISSUED BY REPRESENTING CASHINS S ASSOCIATES INcT DAY DATE ISSUED O04Xmdash 1 bull-bullmdashbull f P^JT
PROJECT NAME_ SITE LOCATION
THE PURPOSE OF THE FOLLOWING STATEMENT IS TO DOCUMENT THE EXISTENCE OF A CONDITION OR CONCERN WHICH CASHINS amp ASSOCIATES INC BELIEVES WARRANTS IMMEDIATE CORRECTIVE ACTION POSSIBLE SOLUTIONS AND OR CORRECTIVE ACTIONS WILL BE INCLUDED IN THIS NOTIFICATION WHEN POSSIBLE THIS NOTIFICATION IS LIMITED TO SITUATIONS THAT REPRESENT EITHER IMMEDIATE DANGER TO LIFE OR HEALTH CONDITIONS OR PREVIOUSLY IDENTIFIED CHRONIC PROBLEMS THAT UNDERMINE OUR ABILITY TO EFFECTIVELY INSURE COMPLIANCE WITH THE REQUIREMENTS OF THE HEALTH AND SAFETY PLAN
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Industrial Hygirne amp Cmimnmtntal Testing
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
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LOCATION Salem Acres Superfund Site SL-4 Area
DATES INCLUDED IN SUMMARY T
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07161996 1650 617944408 CASHING 3 ASSOCIATES PAGE 05
CASHINSamp Associates Inc
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CASHINS amp Associates Inc
WBBKLY HEALTH amp SAFETY FLAK COMPLIANCE SUMMARY REPORT
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- barcode 14732
- barcodetext SEMS Doc ID 14732
![Page 23: SALEM ACRES SUPERFUND SITE SALEM, MA ...The truck loading pa d consisted of a crushed stone are sea t up along the east sid e o f SL-4 adjacent to the access road A. row of concrete](https://reader036.vdocuments.us/reader036/viewer/2022070114/60729b840fec4e6b4d136a16/html5/thumbnails/23.jpg)
(7)
TRUCK LOADING PAD LOOKING NORTHWEST FROM SUPPORT ZONE
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(8)
DECONTAMINATION PAD LOOKING NORTHWEST FROM SUPPORT ZONE
(9)
EXCAVATION OF FLY ASH LOOKING NORTHWEST FROM CRZ NOTE WATER FOR DUST CONTROL
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(10)
VIEW LOOKING WEST AFTER REMOVAL OF FLY ASH NOTE WA-1 BEYOND EROSION CONTROLS
(11)
EXCAVATION OF CONTAMINATED OVERBURDEN LOOKING SOUTH FROM DA-1 BOUNDARY
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(12)
VIEW OF RESTORED SITE LOOKING WEST TOWARD WA-1
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VIEW OF RESTORED SITE LOOKING NORTH TOWARD DA-1 ALONG ACCESS ROAD
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(15)
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ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(18)
VIEW OF RESTORED SITE ON DA-1 SIDE OF FENCE - LOOKING WEST SL-4 ON RIGHT
APPENDIX A
ANALYTICAL RESULTS FOR
PONDED WATER
110795 1638 copy617 890 3883 TMA-WALTHAM ] 002007
PRELIMINARY REPORT UNAUDITED RESULTS
Thenno Analytical 300 Second Avenue PO Box 521 Waltham HA 02254
Attn Client Services Phone (617) 890-7200
Cashins amp Associates Order S5-11-034 55 Cambridge Street Date 110795 1522 Burlington HA 01803 Work ID Salem Acres Water
Date Received 110295 Attn Bob Cashins Date Completed
Purchase Order NA Invoice Number Client Code CASHINS
SAMPLE IDENTIFICATION
Sample Sample Number Description 01 11019S-924-01A
Sample Number 04
Sample Description
110195-9Z4-01D 02 110195-924-01B 05 110195-924-01E 03 110195-924-01C
Certified By
110795 1638 copy617 890 3883 TMA-WALTHAM 003007
PRELIMINARY REPORT UNAUDITED RESULTS
Order f S5-11-034 Thermo Analytical Page 2 110795 1522 TEST RESULTS BY SAHPLE
Test Description Volatile Organics- Aqueous Method EPA_8240 Test Code Collected 110195 02-00 Category WATER
DATE INJECTED 110695 DILUTION FACTOR 100 All results reported 1n ugL
COMPOUND RESULT DET LIMIT COMPOUND RESULT
Chloromethane U 10 Broroodi chl oromethane U Vinyl Chloride U 10 2-Chloroethyl Vinyl Ether U
Bromxnethane U 10 4-dethyl -2-pentanone U Chloroethane U 10 c1 3-1 3-Di chl oropropene U
Trichlorofluoronwthane U 50 Tol uene U Acetone 17 10 trans-1 3-Di chl oropropene LI
11-Oichloroethene U 50 11 2-Tri chl oroethane J Carbon Dlsulfide U 50 2-Hexanone U
Methyl ene Chloride U 50 Tetrachl oroethene U 12-Oichloroethene (total) U 50 D1 bromochl oromethane U
11-01 Chloroethane U 50 Chlorobenzene U Vinyl Acetate U 10 Ethyl benzene U
2-Butanone U 10 in and p-Xylene U Chloroform U 50 o-Xylene U
111-Tri Chloroethane U 50 Styrene U Carbon Tetrachlortde U 50 Broraoform U
Benzene U 50 112 2-Tat rachl oroethane U 12-01 Chloroethane U 50 1 3-01 chl orobenzene U
Trichloroethene U 50 I 4-Di chl orobenzene U 12-Dichloropropane U 50 12-01 chl orobenzene U
SURROGATE STANDARDS RESULT LEVEL X RECOVERY
12-Dichloroethane-D4 52 50 104 Toluene-08 47 50 94
l-Bromo-4-fluorobenzene 56 50 112
NOTES AND DEFINITIONS FOR THIS REPORT U =bull Undetected at stated detection limit
VOAJI
OET LIMIT
50 50
10 50 50 50 50 10
5 0 50 5 0 5 0 50 50 50 50 50 50 50 50
110795 1639 copy617 890 3883 TMA-WALTHAM copy004007
PRELIMINARY REPORT UNAUDITED RESULTS
Order t S5-11-034 Thermo Analytical Page 4 110795 1522 TEST RESULTS BY SAMPLE
ianple Description 110195-924-010 Lab No 04A Test Description RCRA Metals 1n Water Method SW846 Test Code
Collected 110195 0200 Category WATER
METAL RESULT DETECTION LIMIT METAL RESULT DETECTION LIMIT
Ag Silver U 10 As Arsenic 870 50
Ba Bar inn B69 10 Pb Lead U 50
Cd Cadmium U 50 Se Sel en1 um Z15 50
Cr Chromi um U 20 Hg Mercury U 020
NOTES AND DEFINITIONS FOR THIS REPORT All results reported in ugL U gt Undetected at stated detection limit
110795 1640 Q617 890 3883 TMA-WALTHAM 0005007
PRELIMINARY REPORT UNAUDITED RESULTS
Order S5-11-034 Thermo Analytical Page 5 110795 1522 REGULAR TEST RESULTS BY TEST
Chemical Oxygen Demand Mlnimun Maximum Method EPA600 4101
Sap Sample Description Result Units Limit Prepared Analyzed By 05A 110195-924-01E 64 bullgL 50 110395 110395 JD
Petroleum Hydrocarbons-H20 Minimum Maximum Method EPA600 4181
Samp Sample Description Result Units Limit Prepared Analyzed By 01A 110195-924-01A 108 mgL 050 110395 110395 JO
110795 1640 reg617 890 3883 TMA-WALTHAM copy006007
PRELIMINARY REPORT UNAUDITED RESULTS
Order I S5-11-034 Therm Analytical Page 6 110795 1522 TEST METHODOLOGIES
USEPA Test Methods for Evaluating Solid Wastes (SUS46 Third Edition) Method 7470 - Preparation of water for Mercury analysis
USEPA Test Methods for Evaluating Solid Vastes (SW846 Third Edition) Method 3010 - Add digestion of aqueous samples and extracts for total metals for analysis by Flame Atomic Absorption Spectroscopy or Inductively Coupled Plasma Spectroscopy
USEPA Test Methods for Evaluating Solid Vastes (SWB46 Third Edition Method 8270 mdash Gas ChroroatographyMass Spectrometry for PAHs
Volatile Organics in Water - Hazardous Substance List
SV846 Method 8240 - Modified
Test Methods for Evaluating Solid Waste SU-846 US EPA Office of Solid Waste and Emergency Response Washington 3rd Edition
Aqueous sanples are analyzed in accordance with Method 8240 using a purge and trap technique followed by 64s ChromatographyMass Spectroscopy
Quality assurance procedures for GCMS Include daily tuning and calibration of the mass spectrometer and the use of surrogate standards in each sample to monitor method performance Quantitatton is performed by the Internal standard method Analysis of blanks duplicate samples and standards are run frequently as further quality assurance procedures
USEPA Test Methods for Evaluating Solid Wastes (SW846 Third Edition) Method 3S10 mdash Separatory Funnel Liquid-Liquid Extraction
EPA-6004-79-020 - Chemical Oxygen Demand - Titrimetric Mid-Level Method 4101
EPA6004-79-020 - Petroleum Hydrocarbons 1n Water Total Recoverable Method 4181 (Spectrophotometric Infrared)
110795 1641 copy617 890 3883 TMA-WALTHAM copy007007
APPENDIX B
QUANTITY SURVEY DOCUMENTATION
TFMORAN INC Surveying - Engineering - Land Planning SoilsWetlands Mapping - Landscape Architecture
January 15 1996
Mr Jack Enos Vice President TFord Company Inc 118 Tenney Street Georgetown MA 01833
RE Survey Results - Salem Acres - SL4 Area Salem Massachusetts
Dear Jack
This letter amends the letter of December 13 1995 per our review last week
TFMoran Inc performed topographic surveys at the Salem Acres site on April 21 1994 for GEI Consultants prior to removal of material and for TFord Company on October 18 1995 after the removal of material The survey data from the original survey in 1994 was adjusted thirty feet higher to correct for a datum difference from current site datum This was due to the original reporting of the Site Benchmark (TP34) elevation as 11464 rather than 14464 which is the correct elevation
Once both topographic surfaces were on the site datum the raw cut volume was obtained by Eaglepoint (Volumes Module) Software utilizing the prismoidal method comparing the two surfaces For reference please see the attached topographic plan which superimposes the October 15 1995 contours (dark lines) over the April 21 1994 contours The volume is based on the intersection of the two surfaces Also it was noted that stock piles of material did exist on site which were not surveyed at the time
The final raw cut volume arrived at by the above methods is 12749 Cubic Yards
In November and December of 1995 the site was resurveyed to locate the area of exposed ledge at the site The results of this survey are shown on the attached topographic worksheet dated November 3 1995 and last revised January 15 1996 The results of the survey indicate the total site area to be 50860 sq ft or 117 acres The total area of exposed ledge surveyed is 19990 sq ft or 46 acres If you have any questions regarding the above call me directly Thank you
Sincerely
John W Myhaver Jr ^_ Field Operations Manager
Enclosure ItorLltr
Route 101 Bedford NH 03110 Phone (603) 472-4488 FAX (603) 472-9747
APPENDIX C
HEALTH AND SAFETY PHASE-OUT REPORT
HEALTH AND SAFETY PHASE-OUT REPORT SALEM ACRES SL-4 AREA
Introduction
During remediation work on SL-4 Health and Safety Monitoring was performed Cashins amp Associates Inc of Reading MA performed the following work as a subcontractor to TFCI
1) Preparation of a site-specific Health and Safety Plan (dated September 1 1995)
2) Provide a Field TechnicianIndustrial Hygienist to serve as Site Safety and Health Officer (SSHO) and to conduct air and noise monitoring
3) Provide a Certified Industrial Hygienist to review Health and Safety and to conduct site specific training (record of training included at end of Appendix C)
4) Collect 8-hour air samples for worker exposure and ambient air at the Barcelona Avenue gate Arrange for analysis of the samples and report results
5) Prepare daily and weekly Health and Safety reports
6) Prepare a Health and Safety Phase-Out Report
In general the following health and safety practices were followed
1) All workers wore hard hats safety glasses work boots gloves and hearing protection as minimum level PPE
2) When working in the exclusion zone workers wore in addition to above tyvek rubber overboots and rubber coated gloves When dust was a potential concern an industrial grade dustmist mask was also worn This level of PPE was considered Level D modified
3) Workers leaving the exclusion zone removed PPE (tyveks gloves boots and masks) in the support zone and either disposed of the items or decontaminated them
4) Workers andor visitors without 40-hour OSHA training were not permitted to enter the exclusion zone
Attached is a report prepared by Cashins amp Associates along with weekly Health and Safety Summary Reports prepared by the Field Hygienist In summary the air monitoring results indicate no levels exceeding the applicable exposure guidelines except one instance
During excavation of contaminated overburden in the northwest comer of the site an area of VOC contaminated soil was encountered Total VOCs levels measured using a PID exceeded the action level established in the Health and Safety Plan The SSHO advised TFCI to upgrade to Level C PPE in order to backfill the excavation in this area TFCI equipment operator upgraded and backfilled the area The SSHO in consultation with the Cashins CIH advised TFCI to avoid work in this area until the contaminants were characterized GEI sampled the material for waste characterization analysis and provided the results to TFCI Based on the results an action level was established by the CIH for the specific contaminants found Further PID measurements indicated levels below the new action level and work was resumed
The noise monitoring indicated that the noise level at the Barcelona Avenue gate was not exceeded Only one instance of excess noise level in the work zone was recorded (10 db(a) above the ambient noise level or 85 db(a)) Workers wore hearing protection in this instance
mdash 07171996 1601 6179444032 CASHIMS S ASSOCIATES PAGE 02
CASHINS amp Associates Inc
ItxhalrM Hy-gifnr A Invtronmtnltl Tttling
July 17 1996
Mr Jack Enos T Ford Company Inc USTenney Street Georgetown MA 01833
Dear Jack
The Site Safety and Health Officer (SSHO) from Cashing amp Associates Inc performed daily inspections of the SL-4 area Salem Acres Superfund Site between 9595 and 12195 in accordance with the Health amp Safety Plan (HSP) for the site Daily inspection logs were submitted every day No accidentsincidents were reported during the work period
In accordance with the Health amp Safety Plan the SSHO performed daily air and noise monitoring at the site during Ac project Samples were collected for metals (lead beryllium chromium arsenic) and Polynuclear Aromatic Hydrocarbons (PAHs) at the site perimeter and for workers exposure determination Coal Tar Pitch Volatiles (a benzene soluble extractables) were also used to determine the workers exposure to PAH compounds Coal Tar Pitch Volatiles (CTPV) were analyzed using OSHA 58 Method If CTPV levels oq personal samples exceed the site criteria of 02 ragm3 the sample was submitted for PAHs analysis All air samples on the site perimeter were analyzed for PAH compounds
Site monitoring air sample collection and results report were done under the supervision of a Certified Industrial Hygienist
Full shift personal worker exposure samples were collected once a week Ambient air samples were collected at the Barcelona Avenue gate about 20 feet to the west of the site gate to determine if site contaminants were migrating off site The ambient air samples were also collected once a week during the project except on rainy days and days without work with contaminated soil
All air samples were analyzed by the American Industrial Hygiene Association accredited ESA Laboratories Inc using the following methods PAHs - NIOSH 5515 Lead - NIOSH 7082 Beryllium - NIOSH 7102 Chromium - NIOSH 7024 Arsenic - NIOSH 7900 Coal Tar Pitch Volatiles - OSHA 58 All methods used are accepted by the industrial hygiene community for 8-hour exposure assessment EPA methods are usually used for ambient air measurements
CRErORTTFOmiOO
80 Mam Street bull Reading MA 01867 bull Phone- 61 7-944-4060 bull Fax 61 7-944-4082
07171996 1601 6179444032 CASHIMS amp ASSOCIATES PAGE 03
The results of air samples for metals and PAHs are presented in Table No 1
All concentrations of metals and PAHs at the site perimeter (Barcelona Avenue) and active work zones were below the OSHA Permissible Exposure Limits (PEL) and the American Conference of Governmental Industrial Hygicnists Threshold Limit Value (ACGIH TLV) Two personal samples collected on October 19 and October 23rd showed Coal Tar Pitch Volatiles (CTPV) results above OSHA PEL and AIHA TLV limits Both samples were resubmittcd to the lab for further analysis to determine if PAH compounds are present because the CTPV results were above site criteria
The results of the PAH concentrations for the personal sample on Mark Goodwin on October 19 1995 during excavation and washing trucks and for the personal sample on Ron Maker on October 23 1995 during excavating and cleaning rocks by compressed air were below OSHA PEL and ACGIH TLV limits
The SSHO performed noise monitoring according to the HSP at the exclusion zone and at the Barcelona Avenue site perimeter fence A Dupont sound level meter was used for noise monitoring The noise level in the exclusion zone during all operations except one did not exceed the on site criteria of 85 dB(a) During a short time when the air compressor had been used to clean rocks the sound level in the exclusion zone next to the air compressor did exceed 85 dB(a) Ear protection devices were worn by the workers during that operation At no time did the noise level at the Barcelona Avenue site perimeter exceed 10 dB(a) above the ambient noise level or 85 dB(a)
The SSHO performed total dust monitoring on a daily basis during the project at the site perimeter downwind of work location and at the site gate using a Miniram real time dust meter The summary of dust monitoring is presented in Table No 2 Total dust concentrations on site and off site did not exceed site criteria of 1 mgm3 and the action level of 05 nigny1
The summary of air monitoring for Volatile Organic Compounds (VOC) is presented in Table No 3 VOC concentrations in the working area did not exceed the on site criteria of 5 ppm in a breathing zone VOC concentrations on the site perimeter did not exceed real time off site criteria of 2 ppm
Five detail reports with results of air sampling were submitted during the project period
Sincerely Cashins amp Associates Inc
Evelina Vaughan Industrial Hygieflfst
CASHINS amp ASSOCIATES Inc
80 Mam Street bull Reading MA 01867 bull Phone61 7-944-4060 bull Fax 617-944-4082
07171996 1601 6179444082 CASHINS S ASSOCIATES PAGE 04
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CASHINS amp Associates inc
Ifxtuitral Hygltne A fnvironmtnltt Tuning
W3SXLY HBALTH amp SAFETY PLAN COMPLIANCE SUMMARY R3PORT
CLIENT T foyd C o m a n
LOCATION gal era Acres Sx^perfund Site 8L-4 Area
DATES INCLUDED IN SUMMARY
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SUMMARIZED BY FOR CASHINS amp ASSOCIATES INC
55 CAMBRIDGE STREET bull SUITE 201 bull BURLINGTON MA 01803 laquo TEL 61 -273-9080 bull FAX 67-273-9C84
09111995 1023 6172739084 CASHINS ASSOCIATES PAGE 01
CASHINSamp Associates Inc
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WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Fprd Company
LOCATION Salen Acres Suoerfund Site SL-4 Area
DATES INCLUDED IN SUMMARY
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CASHINS amp Associates Inc
Industrial Hygitnf amp CmimnmenUl Tinting
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Compan
LOCATION Salem Acres Superfund Site SL-4 Area
DATES INCLUDED IN SUMMARY
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CASHINSamp Associates Inc
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WEEKLY HEALTH 6 SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Fortjl Cqjapany
LOCATION Salem Acrlaquoa Superfund Site 9L-4 Area
DATES INCLUDED IN SUMMARY
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WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
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LOCATION Salem Acres Superfund Site SL-4 Area
DATES INCLUDED IN SUMMARY J_
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ISSUED TO REPRESENTING
ISSUED BY REPRESENTING CASHINS S ASSOCIATES INcT DAY DATE ISSUED O04Xmdash 1 bull-bullmdashbull f P^JT
PROJECT NAME_ SITE LOCATION
THE PURPOSE OF THE FOLLOWING STATEMENT IS TO DOCUMENT THE EXISTENCE OF A CONDITION OR CONCERN WHICH CASHINS amp ASSOCIATES INC BELIEVES WARRANTS IMMEDIATE CORRECTIVE ACTION POSSIBLE SOLUTIONS AND OR CORRECTIVE ACTIONS WILL BE INCLUDED IN THIS NOTIFICATION WHEN POSSIBLE THIS NOTIFICATION IS LIMITED TO SITUATIONS THAT REPRESENT EITHER IMMEDIATE DANGER TO LIFE OR HEALTH CONDITIONS OR PREVIOUSLY IDENTIFIED CHRONIC PROBLEMS THAT UNDERMINE OUR ABILITY TO EFFECTIVELY INSURE COMPLIANCE WITH THE REQUIREMENTS OF THE HEALTH AND SAFETY PLAN
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Industrial Hygirne amp Cmimnmtntal Testing
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
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LOCATION Salem Acres Superfund Site SL-4 Area
DATES INCLUDED IN SUMMARY T
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DATES INCLUDED IN SUMMARY bull
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CASHINSamp Associates Inc
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OVSHINSamp Associates Inc
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Company T
LOCATION Salem AcrM Suoerfund Stta 8L-4 Araa
DATES INCLUDED IN SUMMARY
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55 CAMBRIDGE STREET bull SUITE 201 bull 8URUNGTON MA 01803 bull TEL 617-273-9080 bull FAX 617-273-90W
07151996 18 fO 6179444082 CASHINS S ASSOCIATES PAGE 02
CASHINS amp Associates Inc
WBBKLY HEALTH amp SAFETY FLAK COMPLIANCE SUMMARY REPORT
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- barcode 14732
- barcodetext SEMS Doc ID 14732
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(9)
EXCAVATION OF FLY ASH LOOKING NORTHWEST FROM CRZ NOTE WATER FOR DUST CONTROL
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(10)
VIEW LOOKING WEST AFTER REMOVAL OF FLY ASH NOTE WA-1 BEYOND EROSION CONTROLS
(11)
EXCAVATION OF CONTAMINATED OVERBURDEN LOOKING SOUTH FROM DA-1 BOUNDARY
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
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ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
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ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(18)
VIEW OF RESTORED SITE ON DA-1 SIDE OF FENCE - LOOKING WEST SL-4 ON RIGHT
APPENDIX A
ANALYTICAL RESULTS FOR
PONDED WATER
110795 1638 copy617 890 3883 TMA-WALTHAM ] 002007
PRELIMINARY REPORT UNAUDITED RESULTS
Thenno Analytical 300 Second Avenue PO Box 521 Waltham HA 02254
Attn Client Services Phone (617) 890-7200
Cashins amp Associates Order S5-11-034 55 Cambridge Street Date 110795 1522 Burlington HA 01803 Work ID Salem Acres Water
Date Received 110295 Attn Bob Cashins Date Completed
Purchase Order NA Invoice Number Client Code CASHINS
SAMPLE IDENTIFICATION
Sample Sample Number Description 01 11019S-924-01A
Sample Number 04
Sample Description
110195-9Z4-01D 02 110195-924-01B 05 110195-924-01E 03 110195-924-01C
Certified By
110795 1638 copy617 890 3883 TMA-WALTHAM 003007
PRELIMINARY REPORT UNAUDITED RESULTS
Order f S5-11-034 Thermo Analytical Page 2 110795 1522 TEST RESULTS BY SAHPLE
Test Description Volatile Organics- Aqueous Method EPA_8240 Test Code Collected 110195 02-00 Category WATER
DATE INJECTED 110695 DILUTION FACTOR 100 All results reported 1n ugL
COMPOUND RESULT DET LIMIT COMPOUND RESULT
Chloromethane U 10 Broroodi chl oromethane U Vinyl Chloride U 10 2-Chloroethyl Vinyl Ether U
Bromxnethane U 10 4-dethyl -2-pentanone U Chloroethane U 10 c1 3-1 3-Di chl oropropene U
Trichlorofluoronwthane U 50 Tol uene U Acetone 17 10 trans-1 3-Di chl oropropene LI
11-Oichloroethene U 50 11 2-Tri chl oroethane J Carbon Dlsulfide U 50 2-Hexanone U
Methyl ene Chloride U 50 Tetrachl oroethene U 12-Oichloroethene (total) U 50 D1 bromochl oromethane U
11-01 Chloroethane U 50 Chlorobenzene U Vinyl Acetate U 10 Ethyl benzene U
2-Butanone U 10 in and p-Xylene U Chloroform U 50 o-Xylene U
111-Tri Chloroethane U 50 Styrene U Carbon Tetrachlortde U 50 Broraoform U
Benzene U 50 112 2-Tat rachl oroethane U 12-01 Chloroethane U 50 1 3-01 chl orobenzene U
Trichloroethene U 50 I 4-Di chl orobenzene U 12-Dichloropropane U 50 12-01 chl orobenzene U
SURROGATE STANDARDS RESULT LEVEL X RECOVERY
12-Dichloroethane-D4 52 50 104 Toluene-08 47 50 94
l-Bromo-4-fluorobenzene 56 50 112
NOTES AND DEFINITIONS FOR THIS REPORT U =bull Undetected at stated detection limit
VOAJI
OET LIMIT
50 50
10 50 50 50 50 10
5 0 50 5 0 5 0 50 50 50 50 50 50 50 50
110795 1639 copy617 890 3883 TMA-WALTHAM copy004007
PRELIMINARY REPORT UNAUDITED RESULTS
Order t S5-11-034 Thermo Analytical Page 4 110795 1522 TEST RESULTS BY SAMPLE
ianple Description 110195-924-010 Lab No 04A Test Description RCRA Metals 1n Water Method SW846 Test Code
Collected 110195 0200 Category WATER
METAL RESULT DETECTION LIMIT METAL RESULT DETECTION LIMIT
Ag Silver U 10 As Arsenic 870 50
Ba Bar inn B69 10 Pb Lead U 50
Cd Cadmium U 50 Se Sel en1 um Z15 50
Cr Chromi um U 20 Hg Mercury U 020
NOTES AND DEFINITIONS FOR THIS REPORT All results reported in ugL U gt Undetected at stated detection limit
110795 1640 Q617 890 3883 TMA-WALTHAM 0005007
PRELIMINARY REPORT UNAUDITED RESULTS
Order S5-11-034 Thermo Analytical Page 5 110795 1522 REGULAR TEST RESULTS BY TEST
Chemical Oxygen Demand Mlnimun Maximum Method EPA600 4101
Sap Sample Description Result Units Limit Prepared Analyzed By 05A 110195-924-01E 64 bullgL 50 110395 110395 JD
Petroleum Hydrocarbons-H20 Minimum Maximum Method EPA600 4181
Samp Sample Description Result Units Limit Prepared Analyzed By 01A 110195-924-01A 108 mgL 050 110395 110395 JO
110795 1640 reg617 890 3883 TMA-WALTHAM copy006007
PRELIMINARY REPORT UNAUDITED RESULTS
Order I S5-11-034 Therm Analytical Page 6 110795 1522 TEST METHODOLOGIES
USEPA Test Methods for Evaluating Solid Wastes (SUS46 Third Edition) Method 7470 - Preparation of water for Mercury analysis
USEPA Test Methods for Evaluating Solid Vastes (SW846 Third Edition) Method 3010 - Add digestion of aqueous samples and extracts for total metals for analysis by Flame Atomic Absorption Spectroscopy or Inductively Coupled Plasma Spectroscopy
USEPA Test Methods for Evaluating Solid Vastes (SWB46 Third Edition Method 8270 mdash Gas ChroroatographyMass Spectrometry for PAHs
Volatile Organics in Water - Hazardous Substance List
SV846 Method 8240 - Modified
Test Methods for Evaluating Solid Waste SU-846 US EPA Office of Solid Waste and Emergency Response Washington 3rd Edition
Aqueous sanples are analyzed in accordance with Method 8240 using a purge and trap technique followed by 64s ChromatographyMass Spectroscopy
Quality assurance procedures for GCMS Include daily tuning and calibration of the mass spectrometer and the use of surrogate standards in each sample to monitor method performance Quantitatton is performed by the Internal standard method Analysis of blanks duplicate samples and standards are run frequently as further quality assurance procedures
USEPA Test Methods for Evaluating Solid Wastes (SW846 Third Edition) Method 3S10 mdash Separatory Funnel Liquid-Liquid Extraction
EPA-6004-79-020 - Chemical Oxygen Demand - Titrimetric Mid-Level Method 4101
EPA6004-79-020 - Petroleum Hydrocarbons 1n Water Total Recoverable Method 4181 (Spectrophotometric Infrared)
110795 1641 copy617 890 3883 TMA-WALTHAM copy007007
APPENDIX B
QUANTITY SURVEY DOCUMENTATION
TFMORAN INC Surveying - Engineering - Land Planning SoilsWetlands Mapping - Landscape Architecture
January 15 1996
Mr Jack Enos Vice President TFord Company Inc 118 Tenney Street Georgetown MA 01833
RE Survey Results - Salem Acres - SL4 Area Salem Massachusetts
Dear Jack
This letter amends the letter of December 13 1995 per our review last week
TFMoran Inc performed topographic surveys at the Salem Acres site on April 21 1994 for GEI Consultants prior to removal of material and for TFord Company on October 18 1995 after the removal of material The survey data from the original survey in 1994 was adjusted thirty feet higher to correct for a datum difference from current site datum This was due to the original reporting of the Site Benchmark (TP34) elevation as 11464 rather than 14464 which is the correct elevation
Once both topographic surfaces were on the site datum the raw cut volume was obtained by Eaglepoint (Volumes Module) Software utilizing the prismoidal method comparing the two surfaces For reference please see the attached topographic plan which superimposes the October 15 1995 contours (dark lines) over the April 21 1994 contours The volume is based on the intersection of the two surfaces Also it was noted that stock piles of material did exist on site which were not surveyed at the time
The final raw cut volume arrived at by the above methods is 12749 Cubic Yards
In November and December of 1995 the site was resurveyed to locate the area of exposed ledge at the site The results of this survey are shown on the attached topographic worksheet dated November 3 1995 and last revised January 15 1996 The results of the survey indicate the total site area to be 50860 sq ft or 117 acres The total area of exposed ledge surveyed is 19990 sq ft or 46 acres If you have any questions regarding the above call me directly Thank you
Sincerely
John W Myhaver Jr ^_ Field Operations Manager
Enclosure ItorLltr
Route 101 Bedford NH 03110 Phone (603) 472-4488 FAX (603) 472-9747
APPENDIX C
HEALTH AND SAFETY PHASE-OUT REPORT
HEALTH AND SAFETY PHASE-OUT REPORT SALEM ACRES SL-4 AREA
Introduction
During remediation work on SL-4 Health and Safety Monitoring was performed Cashins amp Associates Inc of Reading MA performed the following work as a subcontractor to TFCI
1) Preparation of a site-specific Health and Safety Plan (dated September 1 1995)
2) Provide a Field TechnicianIndustrial Hygienist to serve as Site Safety and Health Officer (SSHO) and to conduct air and noise monitoring
3) Provide a Certified Industrial Hygienist to review Health and Safety and to conduct site specific training (record of training included at end of Appendix C)
4) Collect 8-hour air samples for worker exposure and ambient air at the Barcelona Avenue gate Arrange for analysis of the samples and report results
5) Prepare daily and weekly Health and Safety reports
6) Prepare a Health and Safety Phase-Out Report
In general the following health and safety practices were followed
1) All workers wore hard hats safety glasses work boots gloves and hearing protection as minimum level PPE
2) When working in the exclusion zone workers wore in addition to above tyvek rubber overboots and rubber coated gloves When dust was a potential concern an industrial grade dustmist mask was also worn This level of PPE was considered Level D modified
3) Workers leaving the exclusion zone removed PPE (tyveks gloves boots and masks) in the support zone and either disposed of the items or decontaminated them
4) Workers andor visitors without 40-hour OSHA training were not permitted to enter the exclusion zone
Attached is a report prepared by Cashins amp Associates along with weekly Health and Safety Summary Reports prepared by the Field Hygienist In summary the air monitoring results indicate no levels exceeding the applicable exposure guidelines except one instance
During excavation of contaminated overburden in the northwest comer of the site an area of VOC contaminated soil was encountered Total VOCs levels measured using a PID exceeded the action level established in the Health and Safety Plan The SSHO advised TFCI to upgrade to Level C PPE in order to backfill the excavation in this area TFCI equipment operator upgraded and backfilled the area The SSHO in consultation with the Cashins CIH advised TFCI to avoid work in this area until the contaminants were characterized GEI sampled the material for waste characterization analysis and provided the results to TFCI Based on the results an action level was established by the CIH for the specific contaminants found Further PID measurements indicated levels below the new action level and work was resumed
The noise monitoring indicated that the noise level at the Barcelona Avenue gate was not exceeded Only one instance of excess noise level in the work zone was recorded (10 db(a) above the ambient noise level or 85 db(a)) Workers wore hearing protection in this instance
mdash 07171996 1601 6179444032 CASHIMS S ASSOCIATES PAGE 02
CASHINS amp Associates Inc
ItxhalrM Hy-gifnr A Invtronmtnltl Tttling
July 17 1996
Mr Jack Enos T Ford Company Inc USTenney Street Georgetown MA 01833
Dear Jack
The Site Safety and Health Officer (SSHO) from Cashing amp Associates Inc performed daily inspections of the SL-4 area Salem Acres Superfund Site between 9595 and 12195 in accordance with the Health amp Safety Plan (HSP) for the site Daily inspection logs were submitted every day No accidentsincidents were reported during the work period
In accordance with the Health amp Safety Plan the SSHO performed daily air and noise monitoring at the site during Ac project Samples were collected for metals (lead beryllium chromium arsenic) and Polynuclear Aromatic Hydrocarbons (PAHs) at the site perimeter and for workers exposure determination Coal Tar Pitch Volatiles (a benzene soluble extractables) were also used to determine the workers exposure to PAH compounds Coal Tar Pitch Volatiles (CTPV) were analyzed using OSHA 58 Method If CTPV levels oq personal samples exceed the site criteria of 02 ragm3 the sample was submitted for PAHs analysis All air samples on the site perimeter were analyzed for PAH compounds
Site monitoring air sample collection and results report were done under the supervision of a Certified Industrial Hygienist
Full shift personal worker exposure samples were collected once a week Ambient air samples were collected at the Barcelona Avenue gate about 20 feet to the west of the site gate to determine if site contaminants were migrating off site The ambient air samples were also collected once a week during the project except on rainy days and days without work with contaminated soil
All air samples were analyzed by the American Industrial Hygiene Association accredited ESA Laboratories Inc using the following methods PAHs - NIOSH 5515 Lead - NIOSH 7082 Beryllium - NIOSH 7102 Chromium - NIOSH 7024 Arsenic - NIOSH 7900 Coal Tar Pitch Volatiles - OSHA 58 All methods used are accepted by the industrial hygiene community for 8-hour exposure assessment EPA methods are usually used for ambient air measurements
CRErORTTFOmiOO
80 Mam Street bull Reading MA 01867 bull Phone- 61 7-944-4060 bull Fax 61 7-944-4082
07171996 1601 6179444032 CASHIMS amp ASSOCIATES PAGE 03
The results of air samples for metals and PAHs are presented in Table No 1
All concentrations of metals and PAHs at the site perimeter (Barcelona Avenue) and active work zones were below the OSHA Permissible Exposure Limits (PEL) and the American Conference of Governmental Industrial Hygicnists Threshold Limit Value (ACGIH TLV) Two personal samples collected on October 19 and October 23rd showed Coal Tar Pitch Volatiles (CTPV) results above OSHA PEL and AIHA TLV limits Both samples were resubmittcd to the lab for further analysis to determine if PAH compounds are present because the CTPV results were above site criteria
The results of the PAH concentrations for the personal sample on Mark Goodwin on October 19 1995 during excavation and washing trucks and for the personal sample on Ron Maker on October 23 1995 during excavating and cleaning rocks by compressed air were below OSHA PEL and ACGIH TLV limits
The SSHO performed noise monitoring according to the HSP at the exclusion zone and at the Barcelona Avenue site perimeter fence A Dupont sound level meter was used for noise monitoring The noise level in the exclusion zone during all operations except one did not exceed the on site criteria of 85 dB(a) During a short time when the air compressor had been used to clean rocks the sound level in the exclusion zone next to the air compressor did exceed 85 dB(a) Ear protection devices were worn by the workers during that operation At no time did the noise level at the Barcelona Avenue site perimeter exceed 10 dB(a) above the ambient noise level or 85 dB(a)
The SSHO performed total dust monitoring on a daily basis during the project at the site perimeter downwind of work location and at the site gate using a Miniram real time dust meter The summary of dust monitoring is presented in Table No 2 Total dust concentrations on site and off site did not exceed site criteria of 1 mgm3 and the action level of 05 nigny1
The summary of air monitoring for Volatile Organic Compounds (VOC) is presented in Table No 3 VOC concentrations in the working area did not exceed the on site criteria of 5 ppm in a breathing zone VOC concentrations on the site perimeter did not exceed real time off site criteria of 2 ppm
Five detail reports with results of air sampling were submitted during the project period
Sincerely Cashins amp Associates Inc
Evelina Vaughan Industrial Hygieflfst
CASHINS amp ASSOCIATES Inc
80 Mam Street bull Reading MA 01867 bull Phone61 7-944-4060 bull Fax 617-944-4082
07171996 1601 6179444082 CASHINS S ASSOCIATES PAGE 04
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Ifxtuitral Hygltne A fnvironmtnltt Tuning
W3SXLY HBALTH amp SAFETY PLAN COMPLIANCE SUMMARY R3PORT
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LOCATION gal era Acres Sx^perfund Site 8L-4 Area
DATES INCLUDED IN SUMMARY
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LOCATION Salen Acres Suoerfund Site SL-4 Area
DATES INCLUDED IN SUMMARY
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Industrial Hygitnf amp CmimnmenUl Tinting
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Compan
LOCATION Salem Acres Superfund Site SL-4 Area
DATES INCLUDED IN SUMMARY
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LOCATION Salem Acres Superfund Site SL-4 Area
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PROJECT NAME_ SITE LOCATION
THE PURPOSE OF THE FOLLOWING STATEMENT IS TO DOCUMENT THE EXISTENCE OF A CONDITION OR CONCERN WHICH CASHINS amp ASSOCIATES INC BELIEVES WARRANTS IMMEDIATE CORRECTIVE ACTION POSSIBLE SOLUTIONS AND OR CORRECTIVE ACTIONS WILL BE INCLUDED IN THIS NOTIFICATION WHEN POSSIBLE THIS NOTIFICATION IS LIMITED TO SITUATIONS THAT REPRESENT EITHER IMMEDIATE DANGER TO LIFE OR HEALTH CONDITIONS OR PREVIOUSLY IDENTIFIED CHRONIC PROBLEMS THAT UNDERMINE OUR ABILITY TO EFFECTIVELY INSURE COMPLIANCE WITH THE REQUIREMENTS OF THE HEALTH AND SAFETY PLAN
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ACKNOWLEDGEMENT OF ISSUANCE OF NOTIFICATION - NAMECOMPANY ^gt j^f^u^^ CASHINS amp ASSOCINC DATE0 IS
55 CAMBRIDGE STREET bull SUITE 201 bull BURLINGTON MA 01 803 bull TEL 61 7-273-9080 bull FAX fgtl 7-273-9084
CISHINS amp Associates Inc
Industrial Hygirne amp Cmimnmtntal Testing
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Company
LOCATION Salem Acres Superfund Site SL-4 Area
DATES INCLUDED IN SUMMARY T
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CASHINSamp Associates Inc
WEEKLY HEALTH amp SA7STT PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Coqpanv
LOCATION Sa^am Acras Super fund 5 jte SL-4 Area
DATES INCLUDED IN SUMMARY bull
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CASHINSamp Associates Inc
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WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT ^ mdash
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LOCATION Salem Acraa Suoerfund Sita 5L-4
DATES INCLUDED IN SUMMARY bull
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07161996 1650 617944408 CASHING 3 ASSOCIATES PAGE 05
CASHINSamp Associates Inc
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WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
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LOCATION t Salam Acraa Suoarfund Site SL-4 Arlaquoa
DATES INCLUDED IN SUMMARYj pound mdashiffofrshy f
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CASHIMS amp ASSOCIATES PAGE 04 07161996 1658 6179444032
OVSHINSamp Associates Inc
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Company T
LOCATION Salem AcrM Suoerfund Stta 8L-4 Araa
DATES INCLUDED IN SUMMARY
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SUMMARIZED BY pound FOR CASHINS amp ASSOCIATES INC
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DATES INCLUDED IN SUMMARY
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CASHINS amp Associates Inc
WBBKLY HEALTH amp SAFETY FLAK COMPLIANCE SUMMARY REPORT
CLIENT T Ford Compapv
LOCATION i Sal am Acrlaquolaquo Suparfund Sita SL-4 Area
DATES INCLUDED IN SUMMARY i bull pound7 mdash
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- barcode 14732
- barcodetext SEMS Doc ID 14732
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(11)
EXCAVATION OF CONTAMINATED OVERBURDEN LOOKING SOUTH FROM DA-1 BOUNDARY
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
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ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
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ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
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VIEW OF RESTORED SITE ON DA-1 SIDE OF FENCE - LOOKING WEST SL-4 ON RIGHT
APPENDIX A
ANALYTICAL RESULTS FOR
PONDED WATER
110795 1638 copy617 890 3883 TMA-WALTHAM ] 002007
PRELIMINARY REPORT UNAUDITED RESULTS
Thenno Analytical 300 Second Avenue PO Box 521 Waltham HA 02254
Attn Client Services Phone (617) 890-7200
Cashins amp Associates Order S5-11-034 55 Cambridge Street Date 110795 1522 Burlington HA 01803 Work ID Salem Acres Water
Date Received 110295 Attn Bob Cashins Date Completed
Purchase Order NA Invoice Number Client Code CASHINS
SAMPLE IDENTIFICATION
Sample Sample Number Description 01 11019S-924-01A
Sample Number 04
Sample Description
110195-9Z4-01D 02 110195-924-01B 05 110195-924-01E 03 110195-924-01C
Certified By
110795 1638 copy617 890 3883 TMA-WALTHAM 003007
PRELIMINARY REPORT UNAUDITED RESULTS
Order f S5-11-034 Thermo Analytical Page 2 110795 1522 TEST RESULTS BY SAHPLE
Test Description Volatile Organics- Aqueous Method EPA_8240 Test Code Collected 110195 02-00 Category WATER
DATE INJECTED 110695 DILUTION FACTOR 100 All results reported 1n ugL
COMPOUND RESULT DET LIMIT COMPOUND RESULT
Chloromethane U 10 Broroodi chl oromethane U Vinyl Chloride U 10 2-Chloroethyl Vinyl Ether U
Bromxnethane U 10 4-dethyl -2-pentanone U Chloroethane U 10 c1 3-1 3-Di chl oropropene U
Trichlorofluoronwthane U 50 Tol uene U Acetone 17 10 trans-1 3-Di chl oropropene LI
11-Oichloroethene U 50 11 2-Tri chl oroethane J Carbon Dlsulfide U 50 2-Hexanone U
Methyl ene Chloride U 50 Tetrachl oroethene U 12-Oichloroethene (total) U 50 D1 bromochl oromethane U
11-01 Chloroethane U 50 Chlorobenzene U Vinyl Acetate U 10 Ethyl benzene U
2-Butanone U 10 in and p-Xylene U Chloroform U 50 o-Xylene U
111-Tri Chloroethane U 50 Styrene U Carbon Tetrachlortde U 50 Broraoform U
Benzene U 50 112 2-Tat rachl oroethane U 12-01 Chloroethane U 50 1 3-01 chl orobenzene U
Trichloroethene U 50 I 4-Di chl orobenzene U 12-Dichloropropane U 50 12-01 chl orobenzene U
SURROGATE STANDARDS RESULT LEVEL X RECOVERY
12-Dichloroethane-D4 52 50 104 Toluene-08 47 50 94
l-Bromo-4-fluorobenzene 56 50 112
NOTES AND DEFINITIONS FOR THIS REPORT U =bull Undetected at stated detection limit
VOAJI
OET LIMIT
50 50
10 50 50 50 50 10
5 0 50 5 0 5 0 50 50 50 50 50 50 50 50
110795 1639 copy617 890 3883 TMA-WALTHAM copy004007
PRELIMINARY REPORT UNAUDITED RESULTS
Order t S5-11-034 Thermo Analytical Page 4 110795 1522 TEST RESULTS BY SAMPLE
ianple Description 110195-924-010 Lab No 04A Test Description RCRA Metals 1n Water Method SW846 Test Code
Collected 110195 0200 Category WATER
METAL RESULT DETECTION LIMIT METAL RESULT DETECTION LIMIT
Ag Silver U 10 As Arsenic 870 50
Ba Bar inn B69 10 Pb Lead U 50
Cd Cadmium U 50 Se Sel en1 um Z15 50
Cr Chromi um U 20 Hg Mercury U 020
NOTES AND DEFINITIONS FOR THIS REPORT All results reported in ugL U gt Undetected at stated detection limit
110795 1640 Q617 890 3883 TMA-WALTHAM 0005007
PRELIMINARY REPORT UNAUDITED RESULTS
Order S5-11-034 Thermo Analytical Page 5 110795 1522 REGULAR TEST RESULTS BY TEST
Chemical Oxygen Demand Mlnimun Maximum Method EPA600 4101
Sap Sample Description Result Units Limit Prepared Analyzed By 05A 110195-924-01E 64 bullgL 50 110395 110395 JD
Petroleum Hydrocarbons-H20 Minimum Maximum Method EPA600 4181
Samp Sample Description Result Units Limit Prepared Analyzed By 01A 110195-924-01A 108 mgL 050 110395 110395 JO
110795 1640 reg617 890 3883 TMA-WALTHAM copy006007
PRELIMINARY REPORT UNAUDITED RESULTS
Order I S5-11-034 Therm Analytical Page 6 110795 1522 TEST METHODOLOGIES
USEPA Test Methods for Evaluating Solid Wastes (SUS46 Third Edition) Method 7470 - Preparation of water for Mercury analysis
USEPA Test Methods for Evaluating Solid Vastes (SW846 Third Edition) Method 3010 - Add digestion of aqueous samples and extracts for total metals for analysis by Flame Atomic Absorption Spectroscopy or Inductively Coupled Plasma Spectroscopy
USEPA Test Methods for Evaluating Solid Vastes (SWB46 Third Edition Method 8270 mdash Gas ChroroatographyMass Spectrometry for PAHs
Volatile Organics in Water - Hazardous Substance List
SV846 Method 8240 - Modified
Test Methods for Evaluating Solid Waste SU-846 US EPA Office of Solid Waste and Emergency Response Washington 3rd Edition
Aqueous sanples are analyzed in accordance with Method 8240 using a purge and trap technique followed by 64s ChromatographyMass Spectroscopy
Quality assurance procedures for GCMS Include daily tuning and calibration of the mass spectrometer and the use of surrogate standards in each sample to monitor method performance Quantitatton is performed by the Internal standard method Analysis of blanks duplicate samples and standards are run frequently as further quality assurance procedures
USEPA Test Methods for Evaluating Solid Wastes (SW846 Third Edition) Method 3S10 mdash Separatory Funnel Liquid-Liquid Extraction
EPA-6004-79-020 - Chemical Oxygen Demand - Titrimetric Mid-Level Method 4101
EPA6004-79-020 - Petroleum Hydrocarbons 1n Water Total Recoverable Method 4181 (Spectrophotometric Infrared)
110795 1641 copy617 890 3883 TMA-WALTHAM copy007007
APPENDIX B
QUANTITY SURVEY DOCUMENTATION
TFMORAN INC Surveying - Engineering - Land Planning SoilsWetlands Mapping - Landscape Architecture
January 15 1996
Mr Jack Enos Vice President TFord Company Inc 118 Tenney Street Georgetown MA 01833
RE Survey Results - Salem Acres - SL4 Area Salem Massachusetts
Dear Jack
This letter amends the letter of December 13 1995 per our review last week
TFMoran Inc performed topographic surveys at the Salem Acres site on April 21 1994 for GEI Consultants prior to removal of material and for TFord Company on October 18 1995 after the removal of material The survey data from the original survey in 1994 was adjusted thirty feet higher to correct for a datum difference from current site datum This was due to the original reporting of the Site Benchmark (TP34) elevation as 11464 rather than 14464 which is the correct elevation
Once both topographic surfaces were on the site datum the raw cut volume was obtained by Eaglepoint (Volumes Module) Software utilizing the prismoidal method comparing the two surfaces For reference please see the attached topographic plan which superimposes the October 15 1995 contours (dark lines) over the April 21 1994 contours The volume is based on the intersection of the two surfaces Also it was noted that stock piles of material did exist on site which were not surveyed at the time
The final raw cut volume arrived at by the above methods is 12749 Cubic Yards
In November and December of 1995 the site was resurveyed to locate the area of exposed ledge at the site The results of this survey are shown on the attached topographic worksheet dated November 3 1995 and last revised January 15 1996 The results of the survey indicate the total site area to be 50860 sq ft or 117 acres The total area of exposed ledge surveyed is 19990 sq ft or 46 acres If you have any questions regarding the above call me directly Thank you
Sincerely
John W Myhaver Jr ^_ Field Operations Manager
Enclosure ItorLltr
Route 101 Bedford NH 03110 Phone (603) 472-4488 FAX (603) 472-9747
APPENDIX C
HEALTH AND SAFETY PHASE-OUT REPORT
HEALTH AND SAFETY PHASE-OUT REPORT SALEM ACRES SL-4 AREA
Introduction
During remediation work on SL-4 Health and Safety Monitoring was performed Cashins amp Associates Inc of Reading MA performed the following work as a subcontractor to TFCI
1) Preparation of a site-specific Health and Safety Plan (dated September 1 1995)
2) Provide a Field TechnicianIndustrial Hygienist to serve as Site Safety and Health Officer (SSHO) and to conduct air and noise monitoring
3) Provide a Certified Industrial Hygienist to review Health and Safety and to conduct site specific training (record of training included at end of Appendix C)
4) Collect 8-hour air samples for worker exposure and ambient air at the Barcelona Avenue gate Arrange for analysis of the samples and report results
5) Prepare daily and weekly Health and Safety reports
6) Prepare a Health and Safety Phase-Out Report
In general the following health and safety practices were followed
1) All workers wore hard hats safety glasses work boots gloves and hearing protection as minimum level PPE
2) When working in the exclusion zone workers wore in addition to above tyvek rubber overboots and rubber coated gloves When dust was a potential concern an industrial grade dustmist mask was also worn This level of PPE was considered Level D modified
3) Workers leaving the exclusion zone removed PPE (tyveks gloves boots and masks) in the support zone and either disposed of the items or decontaminated them
4) Workers andor visitors without 40-hour OSHA training were not permitted to enter the exclusion zone
Attached is a report prepared by Cashins amp Associates along with weekly Health and Safety Summary Reports prepared by the Field Hygienist In summary the air monitoring results indicate no levels exceeding the applicable exposure guidelines except one instance
During excavation of contaminated overburden in the northwest comer of the site an area of VOC contaminated soil was encountered Total VOCs levels measured using a PID exceeded the action level established in the Health and Safety Plan The SSHO advised TFCI to upgrade to Level C PPE in order to backfill the excavation in this area TFCI equipment operator upgraded and backfilled the area The SSHO in consultation with the Cashins CIH advised TFCI to avoid work in this area until the contaminants were characterized GEI sampled the material for waste characterization analysis and provided the results to TFCI Based on the results an action level was established by the CIH for the specific contaminants found Further PID measurements indicated levels below the new action level and work was resumed
The noise monitoring indicated that the noise level at the Barcelona Avenue gate was not exceeded Only one instance of excess noise level in the work zone was recorded (10 db(a) above the ambient noise level or 85 db(a)) Workers wore hearing protection in this instance
mdash 07171996 1601 6179444032 CASHIMS S ASSOCIATES PAGE 02
CASHINS amp Associates Inc
ItxhalrM Hy-gifnr A Invtronmtnltl Tttling
July 17 1996
Mr Jack Enos T Ford Company Inc USTenney Street Georgetown MA 01833
Dear Jack
The Site Safety and Health Officer (SSHO) from Cashing amp Associates Inc performed daily inspections of the SL-4 area Salem Acres Superfund Site between 9595 and 12195 in accordance with the Health amp Safety Plan (HSP) for the site Daily inspection logs were submitted every day No accidentsincidents were reported during the work period
In accordance with the Health amp Safety Plan the SSHO performed daily air and noise monitoring at the site during Ac project Samples were collected for metals (lead beryllium chromium arsenic) and Polynuclear Aromatic Hydrocarbons (PAHs) at the site perimeter and for workers exposure determination Coal Tar Pitch Volatiles (a benzene soluble extractables) were also used to determine the workers exposure to PAH compounds Coal Tar Pitch Volatiles (CTPV) were analyzed using OSHA 58 Method If CTPV levels oq personal samples exceed the site criteria of 02 ragm3 the sample was submitted for PAHs analysis All air samples on the site perimeter were analyzed for PAH compounds
Site monitoring air sample collection and results report were done under the supervision of a Certified Industrial Hygienist
Full shift personal worker exposure samples were collected once a week Ambient air samples were collected at the Barcelona Avenue gate about 20 feet to the west of the site gate to determine if site contaminants were migrating off site The ambient air samples were also collected once a week during the project except on rainy days and days without work with contaminated soil
All air samples were analyzed by the American Industrial Hygiene Association accredited ESA Laboratories Inc using the following methods PAHs - NIOSH 5515 Lead - NIOSH 7082 Beryllium - NIOSH 7102 Chromium - NIOSH 7024 Arsenic - NIOSH 7900 Coal Tar Pitch Volatiles - OSHA 58 All methods used are accepted by the industrial hygiene community for 8-hour exposure assessment EPA methods are usually used for ambient air measurements
CRErORTTFOmiOO
80 Mam Street bull Reading MA 01867 bull Phone- 61 7-944-4060 bull Fax 61 7-944-4082
07171996 1601 6179444032 CASHIMS amp ASSOCIATES PAGE 03
The results of air samples for metals and PAHs are presented in Table No 1
All concentrations of metals and PAHs at the site perimeter (Barcelona Avenue) and active work zones were below the OSHA Permissible Exposure Limits (PEL) and the American Conference of Governmental Industrial Hygicnists Threshold Limit Value (ACGIH TLV) Two personal samples collected on October 19 and October 23rd showed Coal Tar Pitch Volatiles (CTPV) results above OSHA PEL and AIHA TLV limits Both samples were resubmittcd to the lab for further analysis to determine if PAH compounds are present because the CTPV results were above site criteria
The results of the PAH concentrations for the personal sample on Mark Goodwin on October 19 1995 during excavation and washing trucks and for the personal sample on Ron Maker on October 23 1995 during excavating and cleaning rocks by compressed air were below OSHA PEL and ACGIH TLV limits
The SSHO performed noise monitoring according to the HSP at the exclusion zone and at the Barcelona Avenue site perimeter fence A Dupont sound level meter was used for noise monitoring The noise level in the exclusion zone during all operations except one did not exceed the on site criteria of 85 dB(a) During a short time when the air compressor had been used to clean rocks the sound level in the exclusion zone next to the air compressor did exceed 85 dB(a) Ear protection devices were worn by the workers during that operation At no time did the noise level at the Barcelona Avenue site perimeter exceed 10 dB(a) above the ambient noise level or 85 dB(a)
The SSHO performed total dust monitoring on a daily basis during the project at the site perimeter downwind of work location and at the site gate using a Miniram real time dust meter The summary of dust monitoring is presented in Table No 2 Total dust concentrations on site and off site did not exceed site criteria of 1 mgm3 and the action level of 05 nigny1
The summary of air monitoring for Volatile Organic Compounds (VOC) is presented in Table No 3 VOC concentrations in the working area did not exceed the on site criteria of 5 ppm in a breathing zone VOC concentrations on the site perimeter did not exceed real time off site criteria of 2 ppm
Five detail reports with results of air sampling were submitted during the project period
Sincerely Cashins amp Associates Inc
Evelina Vaughan Industrial Hygieflfst
CASHINS amp ASSOCIATES Inc
80 Mam Street bull Reading MA 01867 bull Phone61 7-944-4060 bull Fax 617-944-4082
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Ifxtuitral Hygltne A fnvironmtnltt Tuning
W3SXLY HBALTH amp SAFETY PLAN COMPLIANCE SUMMARY R3PORT
CLIENT T foyd C o m a n
LOCATION gal era Acres Sx^perfund Site 8L-4 Area
DATES INCLUDED IN SUMMARY
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WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Fprd Company
LOCATION Salen Acres Suoerfund Site SL-4 Area
DATES INCLUDED IN SUMMARY
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Industrial Hygitnf amp CmimnmenUl Tinting
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Compan
LOCATION Salem Acres Superfund Site SL-4 Area
DATES INCLUDED IN SUMMARY
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CASHINSamp Associates Inc
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WEEKLY HEALTH 6 SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Fortjl Cqjapany
LOCATION Salem Acrlaquoa Superfund Site 9L-4 Area
DATES INCLUDED IN SUMMARY
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Industrial Hygiene amp Emironmvntal Testing
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Company
LOCATION Salem Acres Superfund Site SL-4 Area
DATES INCLUDED IN SUMMARY J_
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ISSUED TO REPRESENTING
ISSUED BY REPRESENTING CASHINS S ASSOCIATES INcT DAY DATE ISSUED O04Xmdash 1 bull-bullmdashbull f P^JT
PROJECT NAME_ SITE LOCATION
THE PURPOSE OF THE FOLLOWING STATEMENT IS TO DOCUMENT THE EXISTENCE OF A CONDITION OR CONCERN WHICH CASHINS amp ASSOCIATES INC BELIEVES WARRANTS IMMEDIATE CORRECTIVE ACTION POSSIBLE SOLUTIONS AND OR CORRECTIVE ACTIONS WILL BE INCLUDED IN THIS NOTIFICATION WHEN POSSIBLE THIS NOTIFICATION IS LIMITED TO SITUATIONS THAT REPRESENT EITHER IMMEDIATE DANGER TO LIFE OR HEALTH CONDITIONS OR PREVIOUSLY IDENTIFIED CHRONIC PROBLEMS THAT UNDERMINE OUR ABILITY TO EFFECTIVELY INSURE COMPLIANCE WITH THE REQUIREMENTS OF THE HEALTH AND SAFETY PLAN
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CISHINS amp Associates Inc
Industrial Hygirne amp Cmimnmtntal Testing
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Company
LOCATION Salem Acres Superfund Site SL-4 Area
DATES INCLUDED IN SUMMARY T
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WEEKLY HEALTH amp SA7STT PLAN COMPLIANCE SUMMARY REPORT
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LOCATION Sa^am Acras Super fund 5 jte SL-4 Area
DATES INCLUDED IN SUMMARY bull
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07161996 1650 617944408 CASHING 3 ASSOCIATES PAGE 05
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WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Company T
LOCATION Salem AcrM Suoerfund Stta 8L-4 Araa
DATES INCLUDED IN SUMMARY
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CASHINS amp Associates Inc
WBBKLY HEALTH amp SAFETY FLAK COMPLIANCE SUMMARY REPORT
CLIENT T Ford Compapv
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- barcode 14732
- barcodetext SEMS Doc ID 14732
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VIEW OF RESTORED SITE ON DA-1 SIDE OF FENCE - LOOKING WEST SL-4 ON RIGHT
APPENDIX A
ANALYTICAL RESULTS FOR
PONDED WATER
110795 1638 copy617 890 3883 TMA-WALTHAM ] 002007
PRELIMINARY REPORT UNAUDITED RESULTS
Thenno Analytical 300 Second Avenue PO Box 521 Waltham HA 02254
Attn Client Services Phone (617) 890-7200
Cashins amp Associates Order S5-11-034 55 Cambridge Street Date 110795 1522 Burlington HA 01803 Work ID Salem Acres Water
Date Received 110295 Attn Bob Cashins Date Completed
Purchase Order NA Invoice Number Client Code CASHINS
SAMPLE IDENTIFICATION
Sample Sample Number Description 01 11019S-924-01A
Sample Number 04
Sample Description
110195-9Z4-01D 02 110195-924-01B 05 110195-924-01E 03 110195-924-01C
Certified By
110795 1638 copy617 890 3883 TMA-WALTHAM 003007
PRELIMINARY REPORT UNAUDITED RESULTS
Order f S5-11-034 Thermo Analytical Page 2 110795 1522 TEST RESULTS BY SAHPLE
Test Description Volatile Organics- Aqueous Method EPA_8240 Test Code Collected 110195 02-00 Category WATER
DATE INJECTED 110695 DILUTION FACTOR 100 All results reported 1n ugL
COMPOUND RESULT DET LIMIT COMPOUND RESULT
Chloromethane U 10 Broroodi chl oromethane U Vinyl Chloride U 10 2-Chloroethyl Vinyl Ether U
Bromxnethane U 10 4-dethyl -2-pentanone U Chloroethane U 10 c1 3-1 3-Di chl oropropene U
Trichlorofluoronwthane U 50 Tol uene U Acetone 17 10 trans-1 3-Di chl oropropene LI
11-Oichloroethene U 50 11 2-Tri chl oroethane J Carbon Dlsulfide U 50 2-Hexanone U
Methyl ene Chloride U 50 Tetrachl oroethene U 12-Oichloroethene (total) U 50 D1 bromochl oromethane U
11-01 Chloroethane U 50 Chlorobenzene U Vinyl Acetate U 10 Ethyl benzene U
2-Butanone U 10 in and p-Xylene U Chloroform U 50 o-Xylene U
111-Tri Chloroethane U 50 Styrene U Carbon Tetrachlortde U 50 Broraoform U
Benzene U 50 112 2-Tat rachl oroethane U 12-01 Chloroethane U 50 1 3-01 chl orobenzene U
Trichloroethene U 50 I 4-Di chl orobenzene U 12-Dichloropropane U 50 12-01 chl orobenzene U
SURROGATE STANDARDS RESULT LEVEL X RECOVERY
12-Dichloroethane-D4 52 50 104 Toluene-08 47 50 94
l-Bromo-4-fluorobenzene 56 50 112
NOTES AND DEFINITIONS FOR THIS REPORT U =bull Undetected at stated detection limit
VOAJI
OET LIMIT
50 50
10 50 50 50 50 10
5 0 50 5 0 5 0 50 50 50 50 50 50 50 50
110795 1639 copy617 890 3883 TMA-WALTHAM copy004007
PRELIMINARY REPORT UNAUDITED RESULTS
Order t S5-11-034 Thermo Analytical Page 4 110795 1522 TEST RESULTS BY SAMPLE
ianple Description 110195-924-010 Lab No 04A Test Description RCRA Metals 1n Water Method SW846 Test Code
Collected 110195 0200 Category WATER
METAL RESULT DETECTION LIMIT METAL RESULT DETECTION LIMIT
Ag Silver U 10 As Arsenic 870 50
Ba Bar inn B69 10 Pb Lead U 50
Cd Cadmium U 50 Se Sel en1 um Z15 50
Cr Chromi um U 20 Hg Mercury U 020
NOTES AND DEFINITIONS FOR THIS REPORT All results reported in ugL U gt Undetected at stated detection limit
110795 1640 Q617 890 3883 TMA-WALTHAM 0005007
PRELIMINARY REPORT UNAUDITED RESULTS
Order S5-11-034 Thermo Analytical Page 5 110795 1522 REGULAR TEST RESULTS BY TEST
Chemical Oxygen Demand Mlnimun Maximum Method EPA600 4101
Sap Sample Description Result Units Limit Prepared Analyzed By 05A 110195-924-01E 64 bullgL 50 110395 110395 JD
Petroleum Hydrocarbons-H20 Minimum Maximum Method EPA600 4181
Samp Sample Description Result Units Limit Prepared Analyzed By 01A 110195-924-01A 108 mgL 050 110395 110395 JO
110795 1640 reg617 890 3883 TMA-WALTHAM copy006007
PRELIMINARY REPORT UNAUDITED RESULTS
Order I S5-11-034 Therm Analytical Page 6 110795 1522 TEST METHODOLOGIES
USEPA Test Methods for Evaluating Solid Wastes (SUS46 Third Edition) Method 7470 - Preparation of water for Mercury analysis
USEPA Test Methods for Evaluating Solid Vastes (SW846 Third Edition) Method 3010 - Add digestion of aqueous samples and extracts for total metals for analysis by Flame Atomic Absorption Spectroscopy or Inductively Coupled Plasma Spectroscopy
USEPA Test Methods for Evaluating Solid Vastes (SWB46 Third Edition Method 8270 mdash Gas ChroroatographyMass Spectrometry for PAHs
Volatile Organics in Water - Hazardous Substance List
SV846 Method 8240 - Modified
Test Methods for Evaluating Solid Waste SU-846 US EPA Office of Solid Waste and Emergency Response Washington 3rd Edition
Aqueous sanples are analyzed in accordance with Method 8240 using a purge and trap technique followed by 64s ChromatographyMass Spectroscopy
Quality assurance procedures for GCMS Include daily tuning and calibration of the mass spectrometer and the use of surrogate standards in each sample to monitor method performance Quantitatton is performed by the Internal standard method Analysis of blanks duplicate samples and standards are run frequently as further quality assurance procedures
USEPA Test Methods for Evaluating Solid Wastes (SW846 Third Edition) Method 3S10 mdash Separatory Funnel Liquid-Liquid Extraction
EPA-6004-79-020 - Chemical Oxygen Demand - Titrimetric Mid-Level Method 4101
EPA6004-79-020 - Petroleum Hydrocarbons 1n Water Total Recoverable Method 4181 (Spectrophotometric Infrared)
110795 1641 copy617 890 3883 TMA-WALTHAM copy007007
APPENDIX B
QUANTITY SURVEY DOCUMENTATION
TFMORAN INC Surveying - Engineering - Land Planning SoilsWetlands Mapping - Landscape Architecture
January 15 1996
Mr Jack Enos Vice President TFord Company Inc 118 Tenney Street Georgetown MA 01833
RE Survey Results - Salem Acres - SL4 Area Salem Massachusetts
Dear Jack
This letter amends the letter of December 13 1995 per our review last week
TFMoran Inc performed topographic surveys at the Salem Acres site on April 21 1994 for GEI Consultants prior to removal of material and for TFord Company on October 18 1995 after the removal of material The survey data from the original survey in 1994 was adjusted thirty feet higher to correct for a datum difference from current site datum This was due to the original reporting of the Site Benchmark (TP34) elevation as 11464 rather than 14464 which is the correct elevation
Once both topographic surfaces were on the site datum the raw cut volume was obtained by Eaglepoint (Volumes Module) Software utilizing the prismoidal method comparing the two surfaces For reference please see the attached topographic plan which superimposes the October 15 1995 contours (dark lines) over the April 21 1994 contours The volume is based on the intersection of the two surfaces Also it was noted that stock piles of material did exist on site which were not surveyed at the time
The final raw cut volume arrived at by the above methods is 12749 Cubic Yards
In November and December of 1995 the site was resurveyed to locate the area of exposed ledge at the site The results of this survey are shown on the attached topographic worksheet dated November 3 1995 and last revised January 15 1996 The results of the survey indicate the total site area to be 50860 sq ft or 117 acres The total area of exposed ledge surveyed is 19990 sq ft or 46 acres If you have any questions regarding the above call me directly Thank you
Sincerely
John W Myhaver Jr ^_ Field Operations Manager
Enclosure ItorLltr
Route 101 Bedford NH 03110 Phone (603) 472-4488 FAX (603) 472-9747
APPENDIX C
HEALTH AND SAFETY PHASE-OUT REPORT
HEALTH AND SAFETY PHASE-OUT REPORT SALEM ACRES SL-4 AREA
Introduction
During remediation work on SL-4 Health and Safety Monitoring was performed Cashins amp Associates Inc of Reading MA performed the following work as a subcontractor to TFCI
1) Preparation of a site-specific Health and Safety Plan (dated September 1 1995)
2) Provide a Field TechnicianIndustrial Hygienist to serve as Site Safety and Health Officer (SSHO) and to conduct air and noise monitoring
3) Provide a Certified Industrial Hygienist to review Health and Safety and to conduct site specific training (record of training included at end of Appendix C)
4) Collect 8-hour air samples for worker exposure and ambient air at the Barcelona Avenue gate Arrange for analysis of the samples and report results
5) Prepare daily and weekly Health and Safety reports
6) Prepare a Health and Safety Phase-Out Report
In general the following health and safety practices were followed
1) All workers wore hard hats safety glasses work boots gloves and hearing protection as minimum level PPE
2) When working in the exclusion zone workers wore in addition to above tyvek rubber overboots and rubber coated gloves When dust was a potential concern an industrial grade dustmist mask was also worn This level of PPE was considered Level D modified
3) Workers leaving the exclusion zone removed PPE (tyveks gloves boots and masks) in the support zone and either disposed of the items or decontaminated them
4) Workers andor visitors without 40-hour OSHA training were not permitted to enter the exclusion zone
Attached is a report prepared by Cashins amp Associates along with weekly Health and Safety Summary Reports prepared by the Field Hygienist In summary the air monitoring results indicate no levels exceeding the applicable exposure guidelines except one instance
During excavation of contaminated overburden in the northwest comer of the site an area of VOC contaminated soil was encountered Total VOCs levels measured using a PID exceeded the action level established in the Health and Safety Plan The SSHO advised TFCI to upgrade to Level C PPE in order to backfill the excavation in this area TFCI equipment operator upgraded and backfilled the area The SSHO in consultation with the Cashins CIH advised TFCI to avoid work in this area until the contaminants were characterized GEI sampled the material for waste characterization analysis and provided the results to TFCI Based on the results an action level was established by the CIH for the specific contaminants found Further PID measurements indicated levels below the new action level and work was resumed
The noise monitoring indicated that the noise level at the Barcelona Avenue gate was not exceeded Only one instance of excess noise level in the work zone was recorded (10 db(a) above the ambient noise level or 85 db(a)) Workers wore hearing protection in this instance
mdash 07171996 1601 6179444032 CASHIMS S ASSOCIATES PAGE 02
CASHINS amp Associates Inc
ItxhalrM Hy-gifnr A Invtronmtnltl Tttling
July 17 1996
Mr Jack Enos T Ford Company Inc USTenney Street Georgetown MA 01833
Dear Jack
The Site Safety and Health Officer (SSHO) from Cashing amp Associates Inc performed daily inspections of the SL-4 area Salem Acres Superfund Site between 9595 and 12195 in accordance with the Health amp Safety Plan (HSP) for the site Daily inspection logs were submitted every day No accidentsincidents were reported during the work period
In accordance with the Health amp Safety Plan the SSHO performed daily air and noise monitoring at the site during Ac project Samples were collected for metals (lead beryllium chromium arsenic) and Polynuclear Aromatic Hydrocarbons (PAHs) at the site perimeter and for workers exposure determination Coal Tar Pitch Volatiles (a benzene soluble extractables) were also used to determine the workers exposure to PAH compounds Coal Tar Pitch Volatiles (CTPV) were analyzed using OSHA 58 Method If CTPV levels oq personal samples exceed the site criteria of 02 ragm3 the sample was submitted for PAHs analysis All air samples on the site perimeter were analyzed for PAH compounds
Site monitoring air sample collection and results report were done under the supervision of a Certified Industrial Hygienist
Full shift personal worker exposure samples were collected once a week Ambient air samples were collected at the Barcelona Avenue gate about 20 feet to the west of the site gate to determine if site contaminants were migrating off site The ambient air samples were also collected once a week during the project except on rainy days and days without work with contaminated soil
All air samples were analyzed by the American Industrial Hygiene Association accredited ESA Laboratories Inc using the following methods PAHs - NIOSH 5515 Lead - NIOSH 7082 Beryllium - NIOSH 7102 Chromium - NIOSH 7024 Arsenic - NIOSH 7900 Coal Tar Pitch Volatiles - OSHA 58 All methods used are accepted by the industrial hygiene community for 8-hour exposure assessment EPA methods are usually used for ambient air measurements
CRErORTTFOmiOO
80 Mam Street bull Reading MA 01867 bull Phone- 61 7-944-4060 bull Fax 61 7-944-4082
07171996 1601 6179444032 CASHIMS amp ASSOCIATES PAGE 03
The results of air samples for metals and PAHs are presented in Table No 1
All concentrations of metals and PAHs at the site perimeter (Barcelona Avenue) and active work zones were below the OSHA Permissible Exposure Limits (PEL) and the American Conference of Governmental Industrial Hygicnists Threshold Limit Value (ACGIH TLV) Two personal samples collected on October 19 and October 23rd showed Coal Tar Pitch Volatiles (CTPV) results above OSHA PEL and AIHA TLV limits Both samples were resubmittcd to the lab for further analysis to determine if PAH compounds are present because the CTPV results were above site criteria
The results of the PAH concentrations for the personal sample on Mark Goodwin on October 19 1995 during excavation and washing trucks and for the personal sample on Ron Maker on October 23 1995 during excavating and cleaning rocks by compressed air were below OSHA PEL and ACGIH TLV limits
The SSHO performed noise monitoring according to the HSP at the exclusion zone and at the Barcelona Avenue site perimeter fence A Dupont sound level meter was used for noise monitoring The noise level in the exclusion zone during all operations except one did not exceed the on site criteria of 85 dB(a) During a short time when the air compressor had been used to clean rocks the sound level in the exclusion zone next to the air compressor did exceed 85 dB(a) Ear protection devices were worn by the workers during that operation At no time did the noise level at the Barcelona Avenue site perimeter exceed 10 dB(a) above the ambient noise level or 85 dB(a)
The SSHO performed total dust monitoring on a daily basis during the project at the site perimeter downwind of work location and at the site gate using a Miniram real time dust meter The summary of dust monitoring is presented in Table No 2 Total dust concentrations on site and off site did not exceed site criteria of 1 mgm3 and the action level of 05 nigny1
The summary of air monitoring for Volatile Organic Compounds (VOC) is presented in Table No 3 VOC concentrations in the working area did not exceed the on site criteria of 5 ppm in a breathing zone VOC concentrations on the site perimeter did not exceed real time off site criteria of 2 ppm
Five detail reports with results of air sampling were submitted during the project period
Sincerely Cashins amp Associates Inc
Evelina Vaughan Industrial Hygieflfst
CASHINS amp ASSOCIATES Inc
80 Mam Street bull Reading MA 01867 bull Phone61 7-944-4060 bull Fax 617-944-4082
07171996 1601 6179444082 CASHINS S ASSOCIATES PAGE 04
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ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
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VIEW OF RESTORED SITE ON DA-1 SIDE OF FENCE - LOOKING WEST SL-4 ON RIGHT
APPENDIX A
ANALYTICAL RESULTS FOR
PONDED WATER
110795 1638 copy617 890 3883 TMA-WALTHAM ] 002007
PRELIMINARY REPORT UNAUDITED RESULTS
Thenno Analytical 300 Second Avenue PO Box 521 Waltham HA 02254
Attn Client Services Phone (617) 890-7200
Cashins amp Associates Order S5-11-034 55 Cambridge Street Date 110795 1522 Burlington HA 01803 Work ID Salem Acres Water
Date Received 110295 Attn Bob Cashins Date Completed
Purchase Order NA Invoice Number Client Code CASHINS
SAMPLE IDENTIFICATION
Sample Sample Number Description 01 11019S-924-01A
Sample Number 04
Sample Description
110195-9Z4-01D 02 110195-924-01B 05 110195-924-01E 03 110195-924-01C
Certified By
110795 1638 copy617 890 3883 TMA-WALTHAM 003007
PRELIMINARY REPORT UNAUDITED RESULTS
Order f S5-11-034 Thermo Analytical Page 2 110795 1522 TEST RESULTS BY SAHPLE
Test Description Volatile Organics- Aqueous Method EPA_8240 Test Code Collected 110195 02-00 Category WATER
DATE INJECTED 110695 DILUTION FACTOR 100 All results reported 1n ugL
COMPOUND RESULT DET LIMIT COMPOUND RESULT
Chloromethane U 10 Broroodi chl oromethane U Vinyl Chloride U 10 2-Chloroethyl Vinyl Ether U
Bromxnethane U 10 4-dethyl -2-pentanone U Chloroethane U 10 c1 3-1 3-Di chl oropropene U
Trichlorofluoronwthane U 50 Tol uene U Acetone 17 10 trans-1 3-Di chl oropropene LI
11-Oichloroethene U 50 11 2-Tri chl oroethane J Carbon Dlsulfide U 50 2-Hexanone U
Methyl ene Chloride U 50 Tetrachl oroethene U 12-Oichloroethene (total) U 50 D1 bromochl oromethane U
11-01 Chloroethane U 50 Chlorobenzene U Vinyl Acetate U 10 Ethyl benzene U
2-Butanone U 10 in and p-Xylene U Chloroform U 50 o-Xylene U
111-Tri Chloroethane U 50 Styrene U Carbon Tetrachlortde U 50 Broraoform U
Benzene U 50 112 2-Tat rachl oroethane U 12-01 Chloroethane U 50 1 3-01 chl orobenzene U
Trichloroethene U 50 I 4-Di chl orobenzene U 12-Dichloropropane U 50 12-01 chl orobenzene U
SURROGATE STANDARDS RESULT LEVEL X RECOVERY
12-Dichloroethane-D4 52 50 104 Toluene-08 47 50 94
l-Bromo-4-fluorobenzene 56 50 112
NOTES AND DEFINITIONS FOR THIS REPORT U =bull Undetected at stated detection limit
VOAJI
OET LIMIT
50 50
10 50 50 50 50 10
5 0 50 5 0 5 0 50 50 50 50 50 50 50 50
110795 1639 copy617 890 3883 TMA-WALTHAM copy004007
PRELIMINARY REPORT UNAUDITED RESULTS
Order t S5-11-034 Thermo Analytical Page 4 110795 1522 TEST RESULTS BY SAMPLE
ianple Description 110195-924-010 Lab No 04A Test Description RCRA Metals 1n Water Method SW846 Test Code
Collected 110195 0200 Category WATER
METAL RESULT DETECTION LIMIT METAL RESULT DETECTION LIMIT
Ag Silver U 10 As Arsenic 870 50
Ba Bar inn B69 10 Pb Lead U 50
Cd Cadmium U 50 Se Sel en1 um Z15 50
Cr Chromi um U 20 Hg Mercury U 020
NOTES AND DEFINITIONS FOR THIS REPORT All results reported in ugL U gt Undetected at stated detection limit
110795 1640 Q617 890 3883 TMA-WALTHAM 0005007
PRELIMINARY REPORT UNAUDITED RESULTS
Order S5-11-034 Thermo Analytical Page 5 110795 1522 REGULAR TEST RESULTS BY TEST
Chemical Oxygen Demand Mlnimun Maximum Method EPA600 4101
Sap Sample Description Result Units Limit Prepared Analyzed By 05A 110195-924-01E 64 bullgL 50 110395 110395 JD
Petroleum Hydrocarbons-H20 Minimum Maximum Method EPA600 4181
Samp Sample Description Result Units Limit Prepared Analyzed By 01A 110195-924-01A 108 mgL 050 110395 110395 JO
110795 1640 reg617 890 3883 TMA-WALTHAM copy006007
PRELIMINARY REPORT UNAUDITED RESULTS
Order I S5-11-034 Therm Analytical Page 6 110795 1522 TEST METHODOLOGIES
USEPA Test Methods for Evaluating Solid Wastes (SUS46 Third Edition) Method 7470 - Preparation of water for Mercury analysis
USEPA Test Methods for Evaluating Solid Vastes (SW846 Third Edition) Method 3010 - Add digestion of aqueous samples and extracts for total metals for analysis by Flame Atomic Absorption Spectroscopy or Inductively Coupled Plasma Spectroscopy
USEPA Test Methods for Evaluating Solid Vastes (SWB46 Third Edition Method 8270 mdash Gas ChroroatographyMass Spectrometry for PAHs
Volatile Organics in Water - Hazardous Substance List
SV846 Method 8240 - Modified
Test Methods for Evaluating Solid Waste SU-846 US EPA Office of Solid Waste and Emergency Response Washington 3rd Edition
Aqueous sanples are analyzed in accordance with Method 8240 using a purge and trap technique followed by 64s ChromatographyMass Spectroscopy
Quality assurance procedures for GCMS Include daily tuning and calibration of the mass spectrometer and the use of surrogate standards in each sample to monitor method performance Quantitatton is performed by the Internal standard method Analysis of blanks duplicate samples and standards are run frequently as further quality assurance procedures
USEPA Test Methods for Evaluating Solid Wastes (SW846 Third Edition) Method 3S10 mdash Separatory Funnel Liquid-Liquid Extraction
EPA-6004-79-020 - Chemical Oxygen Demand - Titrimetric Mid-Level Method 4101
EPA6004-79-020 - Petroleum Hydrocarbons 1n Water Total Recoverable Method 4181 (Spectrophotometric Infrared)
110795 1641 copy617 890 3883 TMA-WALTHAM copy007007
APPENDIX B
QUANTITY SURVEY DOCUMENTATION
TFMORAN INC Surveying - Engineering - Land Planning SoilsWetlands Mapping - Landscape Architecture
January 15 1996
Mr Jack Enos Vice President TFord Company Inc 118 Tenney Street Georgetown MA 01833
RE Survey Results - Salem Acres - SL4 Area Salem Massachusetts
Dear Jack
This letter amends the letter of December 13 1995 per our review last week
TFMoran Inc performed topographic surveys at the Salem Acres site on April 21 1994 for GEI Consultants prior to removal of material and for TFord Company on October 18 1995 after the removal of material The survey data from the original survey in 1994 was adjusted thirty feet higher to correct for a datum difference from current site datum This was due to the original reporting of the Site Benchmark (TP34) elevation as 11464 rather than 14464 which is the correct elevation
Once both topographic surfaces were on the site datum the raw cut volume was obtained by Eaglepoint (Volumes Module) Software utilizing the prismoidal method comparing the two surfaces For reference please see the attached topographic plan which superimposes the October 15 1995 contours (dark lines) over the April 21 1994 contours The volume is based on the intersection of the two surfaces Also it was noted that stock piles of material did exist on site which were not surveyed at the time
The final raw cut volume arrived at by the above methods is 12749 Cubic Yards
In November and December of 1995 the site was resurveyed to locate the area of exposed ledge at the site The results of this survey are shown on the attached topographic worksheet dated November 3 1995 and last revised January 15 1996 The results of the survey indicate the total site area to be 50860 sq ft or 117 acres The total area of exposed ledge surveyed is 19990 sq ft or 46 acres If you have any questions regarding the above call me directly Thank you
Sincerely
John W Myhaver Jr ^_ Field Operations Manager
Enclosure ItorLltr
Route 101 Bedford NH 03110 Phone (603) 472-4488 FAX (603) 472-9747
APPENDIX C
HEALTH AND SAFETY PHASE-OUT REPORT
HEALTH AND SAFETY PHASE-OUT REPORT SALEM ACRES SL-4 AREA
Introduction
During remediation work on SL-4 Health and Safety Monitoring was performed Cashins amp Associates Inc of Reading MA performed the following work as a subcontractor to TFCI
1) Preparation of a site-specific Health and Safety Plan (dated September 1 1995)
2) Provide a Field TechnicianIndustrial Hygienist to serve as Site Safety and Health Officer (SSHO) and to conduct air and noise monitoring
3) Provide a Certified Industrial Hygienist to review Health and Safety and to conduct site specific training (record of training included at end of Appendix C)
4) Collect 8-hour air samples for worker exposure and ambient air at the Barcelona Avenue gate Arrange for analysis of the samples and report results
5) Prepare daily and weekly Health and Safety reports
6) Prepare a Health and Safety Phase-Out Report
In general the following health and safety practices were followed
1) All workers wore hard hats safety glasses work boots gloves and hearing protection as minimum level PPE
2) When working in the exclusion zone workers wore in addition to above tyvek rubber overboots and rubber coated gloves When dust was a potential concern an industrial grade dustmist mask was also worn This level of PPE was considered Level D modified
3) Workers leaving the exclusion zone removed PPE (tyveks gloves boots and masks) in the support zone and either disposed of the items or decontaminated them
4) Workers andor visitors without 40-hour OSHA training were not permitted to enter the exclusion zone
Attached is a report prepared by Cashins amp Associates along with weekly Health and Safety Summary Reports prepared by the Field Hygienist In summary the air monitoring results indicate no levels exceeding the applicable exposure guidelines except one instance
During excavation of contaminated overburden in the northwest comer of the site an area of VOC contaminated soil was encountered Total VOCs levels measured using a PID exceeded the action level established in the Health and Safety Plan The SSHO advised TFCI to upgrade to Level C PPE in order to backfill the excavation in this area TFCI equipment operator upgraded and backfilled the area The SSHO in consultation with the Cashins CIH advised TFCI to avoid work in this area until the contaminants were characterized GEI sampled the material for waste characterization analysis and provided the results to TFCI Based on the results an action level was established by the CIH for the specific contaminants found Further PID measurements indicated levels below the new action level and work was resumed
The noise monitoring indicated that the noise level at the Barcelona Avenue gate was not exceeded Only one instance of excess noise level in the work zone was recorded (10 db(a) above the ambient noise level or 85 db(a)) Workers wore hearing protection in this instance
mdash 07171996 1601 6179444032 CASHIMS S ASSOCIATES PAGE 02
CASHINS amp Associates Inc
ItxhalrM Hy-gifnr A Invtronmtnltl Tttling
July 17 1996
Mr Jack Enos T Ford Company Inc USTenney Street Georgetown MA 01833
Dear Jack
The Site Safety and Health Officer (SSHO) from Cashing amp Associates Inc performed daily inspections of the SL-4 area Salem Acres Superfund Site between 9595 and 12195 in accordance with the Health amp Safety Plan (HSP) for the site Daily inspection logs were submitted every day No accidentsincidents were reported during the work period
In accordance with the Health amp Safety Plan the SSHO performed daily air and noise monitoring at the site during Ac project Samples were collected for metals (lead beryllium chromium arsenic) and Polynuclear Aromatic Hydrocarbons (PAHs) at the site perimeter and for workers exposure determination Coal Tar Pitch Volatiles (a benzene soluble extractables) were also used to determine the workers exposure to PAH compounds Coal Tar Pitch Volatiles (CTPV) were analyzed using OSHA 58 Method If CTPV levels oq personal samples exceed the site criteria of 02 ragm3 the sample was submitted for PAHs analysis All air samples on the site perimeter were analyzed for PAH compounds
Site monitoring air sample collection and results report were done under the supervision of a Certified Industrial Hygienist
Full shift personal worker exposure samples were collected once a week Ambient air samples were collected at the Barcelona Avenue gate about 20 feet to the west of the site gate to determine if site contaminants were migrating off site The ambient air samples were also collected once a week during the project except on rainy days and days without work with contaminated soil
All air samples were analyzed by the American Industrial Hygiene Association accredited ESA Laboratories Inc using the following methods PAHs - NIOSH 5515 Lead - NIOSH 7082 Beryllium - NIOSH 7102 Chromium - NIOSH 7024 Arsenic - NIOSH 7900 Coal Tar Pitch Volatiles - OSHA 58 All methods used are accepted by the industrial hygiene community for 8-hour exposure assessment EPA methods are usually used for ambient air measurements
CRErORTTFOmiOO
80 Mam Street bull Reading MA 01867 bull Phone- 61 7-944-4060 bull Fax 61 7-944-4082
07171996 1601 6179444032 CASHIMS amp ASSOCIATES PAGE 03
The results of air samples for metals and PAHs are presented in Table No 1
All concentrations of metals and PAHs at the site perimeter (Barcelona Avenue) and active work zones were below the OSHA Permissible Exposure Limits (PEL) and the American Conference of Governmental Industrial Hygicnists Threshold Limit Value (ACGIH TLV) Two personal samples collected on October 19 and October 23rd showed Coal Tar Pitch Volatiles (CTPV) results above OSHA PEL and AIHA TLV limits Both samples were resubmittcd to the lab for further analysis to determine if PAH compounds are present because the CTPV results were above site criteria
The results of the PAH concentrations for the personal sample on Mark Goodwin on October 19 1995 during excavation and washing trucks and for the personal sample on Ron Maker on October 23 1995 during excavating and cleaning rocks by compressed air were below OSHA PEL and ACGIH TLV limits
The SSHO performed noise monitoring according to the HSP at the exclusion zone and at the Barcelona Avenue site perimeter fence A Dupont sound level meter was used for noise monitoring The noise level in the exclusion zone during all operations except one did not exceed the on site criteria of 85 dB(a) During a short time when the air compressor had been used to clean rocks the sound level in the exclusion zone next to the air compressor did exceed 85 dB(a) Ear protection devices were worn by the workers during that operation At no time did the noise level at the Barcelona Avenue site perimeter exceed 10 dB(a) above the ambient noise level or 85 dB(a)
The SSHO performed total dust monitoring on a daily basis during the project at the site perimeter downwind of work location and at the site gate using a Miniram real time dust meter The summary of dust monitoring is presented in Table No 2 Total dust concentrations on site and off site did not exceed site criteria of 1 mgm3 and the action level of 05 nigny1
The summary of air monitoring for Volatile Organic Compounds (VOC) is presented in Table No 3 VOC concentrations in the working area did not exceed the on site criteria of 5 ppm in a breathing zone VOC concentrations on the site perimeter did not exceed real time off site criteria of 2 ppm
Five detail reports with results of air sampling were submitted during the project period
Sincerely Cashins amp Associates Inc
Evelina Vaughan Industrial Hygieflfst
CASHINS amp ASSOCIATES Inc
80 Mam Street bull Reading MA 01867 bull Phone61 7-944-4060 bull Fax 617-944-4082
07171996 1601 6179444082 CASHINS S ASSOCIATES PAGE 04
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CASHINS amp Associates inc
Ifxtuitral Hygltne A fnvironmtnltt Tuning
W3SXLY HBALTH amp SAFETY PLAN COMPLIANCE SUMMARY R3PORT
CLIENT T foyd C o m a n
LOCATION gal era Acres Sx^perfund Site 8L-4 Area
DATES INCLUDED IN SUMMARY
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SUMMARIZED BY FOR CASHINS amp ASSOCIATES INC
55 CAMBRIDGE STREET bull SUITE 201 bull BURLINGTON MA 01803 laquo TEL 61 -273-9080 bull FAX 67-273-9C84
09111995 1023 6172739084 CASHINS ASSOCIATES PAGE 01
CASHINSamp Associates Inc
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WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Fprd Company
LOCATION Salen Acres Suoerfund Site SL-4 Area
DATES INCLUDED IN SUMMARY
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CASHINS amp Associates Inc
Industrial Hygitnf amp CmimnmenUl Tinting
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Compan
LOCATION Salem Acres Superfund Site SL-4 Area
DATES INCLUDED IN SUMMARY
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WEEKLY HEALTH 6 SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Fortjl Cqjapany
LOCATION Salem Acrlaquoa Superfund Site 9L-4 Area
DATES INCLUDED IN SUMMARY
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Industrial Hygiene amp Emironmvntal Testing
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Company
LOCATION Salem Acres Superfund Site SL-4 Area
DATES INCLUDED IN SUMMARY J_
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THE PURPOSE OF THE FOLLOWING STATEMENT IS TO DOCUMENT THE EXISTENCE OF A CONDITION OR CONCERN WHICH CASHINS amp ASSOCIATES INC BELIEVES WARRANTS IMMEDIATE CORRECTIVE ACTION POSSIBLE SOLUTIONS AND OR CORRECTIVE ACTIONS WILL BE INCLUDED IN THIS NOTIFICATION WHEN POSSIBLE THIS NOTIFICATION IS LIMITED TO SITUATIONS THAT REPRESENT EITHER IMMEDIATE DANGER TO LIFE OR HEALTH CONDITIONS OR PREVIOUSLY IDENTIFIED CHRONIC PROBLEMS THAT UNDERMINE OUR ABILITY TO EFFECTIVELY INSURE COMPLIANCE WITH THE REQUIREMENTS OF THE HEALTH AND SAFETY PLAN
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Industrial Hygirne amp Cmimnmtntal Testing
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Company
LOCATION Salem Acres Superfund Site SL-4 Area
DATES INCLUDED IN SUMMARY T
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LOCATION Salem Acraa Suoerfund Sita 5L-4
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WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Company T
LOCATION Salem AcrM Suoerfund Stta 8L-4 Araa
DATES INCLUDED IN SUMMARY
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DATES INCLUDED IN SUMMARY
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55 CAMBRIDGE STREET bull SUITE 201 bull 8URUNGTON MA 01803 bull TEL 617-273-9080 bull FAX 617-273-90W
07151996 18 fO 6179444082 CASHINS S ASSOCIATES PAGE 02
CASHINS amp Associates Inc
WBBKLY HEALTH amp SAFETY FLAK COMPLIANCE SUMMARY REPORT
CLIENT T Ford Compapv
LOCATION i Sal am Acrlaquolaquo Suparfund Sita SL-4 Area
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- barcode 14732
- barcodetext SEMS Doc ID 14732
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ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
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VIEW OF RESTORED SITE ON DA-1 SIDE OF FENCE - LOOKING WEST SL-4 ON RIGHT
APPENDIX A
ANALYTICAL RESULTS FOR
PONDED WATER
110795 1638 copy617 890 3883 TMA-WALTHAM ] 002007
PRELIMINARY REPORT UNAUDITED RESULTS
Thenno Analytical 300 Second Avenue PO Box 521 Waltham HA 02254
Attn Client Services Phone (617) 890-7200
Cashins amp Associates Order S5-11-034 55 Cambridge Street Date 110795 1522 Burlington HA 01803 Work ID Salem Acres Water
Date Received 110295 Attn Bob Cashins Date Completed
Purchase Order NA Invoice Number Client Code CASHINS
SAMPLE IDENTIFICATION
Sample Sample Number Description 01 11019S-924-01A
Sample Number 04
Sample Description
110195-9Z4-01D 02 110195-924-01B 05 110195-924-01E 03 110195-924-01C
Certified By
110795 1638 copy617 890 3883 TMA-WALTHAM 003007
PRELIMINARY REPORT UNAUDITED RESULTS
Order f S5-11-034 Thermo Analytical Page 2 110795 1522 TEST RESULTS BY SAHPLE
Test Description Volatile Organics- Aqueous Method EPA_8240 Test Code Collected 110195 02-00 Category WATER
DATE INJECTED 110695 DILUTION FACTOR 100 All results reported 1n ugL
COMPOUND RESULT DET LIMIT COMPOUND RESULT
Chloromethane U 10 Broroodi chl oromethane U Vinyl Chloride U 10 2-Chloroethyl Vinyl Ether U
Bromxnethane U 10 4-dethyl -2-pentanone U Chloroethane U 10 c1 3-1 3-Di chl oropropene U
Trichlorofluoronwthane U 50 Tol uene U Acetone 17 10 trans-1 3-Di chl oropropene LI
11-Oichloroethene U 50 11 2-Tri chl oroethane J Carbon Dlsulfide U 50 2-Hexanone U
Methyl ene Chloride U 50 Tetrachl oroethene U 12-Oichloroethene (total) U 50 D1 bromochl oromethane U
11-01 Chloroethane U 50 Chlorobenzene U Vinyl Acetate U 10 Ethyl benzene U
2-Butanone U 10 in and p-Xylene U Chloroform U 50 o-Xylene U
111-Tri Chloroethane U 50 Styrene U Carbon Tetrachlortde U 50 Broraoform U
Benzene U 50 112 2-Tat rachl oroethane U 12-01 Chloroethane U 50 1 3-01 chl orobenzene U
Trichloroethene U 50 I 4-Di chl orobenzene U 12-Dichloropropane U 50 12-01 chl orobenzene U
SURROGATE STANDARDS RESULT LEVEL X RECOVERY
12-Dichloroethane-D4 52 50 104 Toluene-08 47 50 94
l-Bromo-4-fluorobenzene 56 50 112
NOTES AND DEFINITIONS FOR THIS REPORT U =bull Undetected at stated detection limit
VOAJI
OET LIMIT
50 50
10 50 50 50 50 10
5 0 50 5 0 5 0 50 50 50 50 50 50 50 50
110795 1639 copy617 890 3883 TMA-WALTHAM copy004007
PRELIMINARY REPORT UNAUDITED RESULTS
Order t S5-11-034 Thermo Analytical Page 4 110795 1522 TEST RESULTS BY SAMPLE
ianple Description 110195-924-010 Lab No 04A Test Description RCRA Metals 1n Water Method SW846 Test Code
Collected 110195 0200 Category WATER
METAL RESULT DETECTION LIMIT METAL RESULT DETECTION LIMIT
Ag Silver U 10 As Arsenic 870 50
Ba Bar inn B69 10 Pb Lead U 50
Cd Cadmium U 50 Se Sel en1 um Z15 50
Cr Chromi um U 20 Hg Mercury U 020
NOTES AND DEFINITIONS FOR THIS REPORT All results reported in ugL U gt Undetected at stated detection limit
110795 1640 Q617 890 3883 TMA-WALTHAM 0005007
PRELIMINARY REPORT UNAUDITED RESULTS
Order S5-11-034 Thermo Analytical Page 5 110795 1522 REGULAR TEST RESULTS BY TEST
Chemical Oxygen Demand Mlnimun Maximum Method EPA600 4101
Sap Sample Description Result Units Limit Prepared Analyzed By 05A 110195-924-01E 64 bullgL 50 110395 110395 JD
Petroleum Hydrocarbons-H20 Minimum Maximum Method EPA600 4181
Samp Sample Description Result Units Limit Prepared Analyzed By 01A 110195-924-01A 108 mgL 050 110395 110395 JO
110795 1640 reg617 890 3883 TMA-WALTHAM copy006007
PRELIMINARY REPORT UNAUDITED RESULTS
Order I S5-11-034 Therm Analytical Page 6 110795 1522 TEST METHODOLOGIES
USEPA Test Methods for Evaluating Solid Wastes (SUS46 Third Edition) Method 7470 - Preparation of water for Mercury analysis
USEPA Test Methods for Evaluating Solid Vastes (SW846 Third Edition) Method 3010 - Add digestion of aqueous samples and extracts for total metals for analysis by Flame Atomic Absorption Spectroscopy or Inductively Coupled Plasma Spectroscopy
USEPA Test Methods for Evaluating Solid Vastes (SWB46 Third Edition Method 8270 mdash Gas ChroroatographyMass Spectrometry for PAHs
Volatile Organics in Water - Hazardous Substance List
SV846 Method 8240 - Modified
Test Methods for Evaluating Solid Waste SU-846 US EPA Office of Solid Waste and Emergency Response Washington 3rd Edition
Aqueous sanples are analyzed in accordance with Method 8240 using a purge and trap technique followed by 64s ChromatographyMass Spectroscopy
Quality assurance procedures for GCMS Include daily tuning and calibration of the mass spectrometer and the use of surrogate standards in each sample to monitor method performance Quantitatton is performed by the Internal standard method Analysis of blanks duplicate samples and standards are run frequently as further quality assurance procedures
USEPA Test Methods for Evaluating Solid Wastes (SW846 Third Edition) Method 3S10 mdash Separatory Funnel Liquid-Liquid Extraction
EPA-6004-79-020 - Chemical Oxygen Demand - Titrimetric Mid-Level Method 4101
EPA6004-79-020 - Petroleum Hydrocarbons 1n Water Total Recoverable Method 4181 (Spectrophotometric Infrared)
110795 1641 copy617 890 3883 TMA-WALTHAM copy007007
APPENDIX B
QUANTITY SURVEY DOCUMENTATION
TFMORAN INC Surveying - Engineering - Land Planning SoilsWetlands Mapping - Landscape Architecture
January 15 1996
Mr Jack Enos Vice President TFord Company Inc 118 Tenney Street Georgetown MA 01833
RE Survey Results - Salem Acres - SL4 Area Salem Massachusetts
Dear Jack
This letter amends the letter of December 13 1995 per our review last week
TFMoran Inc performed topographic surveys at the Salem Acres site on April 21 1994 for GEI Consultants prior to removal of material and for TFord Company on October 18 1995 after the removal of material The survey data from the original survey in 1994 was adjusted thirty feet higher to correct for a datum difference from current site datum This was due to the original reporting of the Site Benchmark (TP34) elevation as 11464 rather than 14464 which is the correct elevation
Once both topographic surfaces were on the site datum the raw cut volume was obtained by Eaglepoint (Volumes Module) Software utilizing the prismoidal method comparing the two surfaces For reference please see the attached topographic plan which superimposes the October 15 1995 contours (dark lines) over the April 21 1994 contours The volume is based on the intersection of the two surfaces Also it was noted that stock piles of material did exist on site which were not surveyed at the time
The final raw cut volume arrived at by the above methods is 12749 Cubic Yards
In November and December of 1995 the site was resurveyed to locate the area of exposed ledge at the site The results of this survey are shown on the attached topographic worksheet dated November 3 1995 and last revised January 15 1996 The results of the survey indicate the total site area to be 50860 sq ft or 117 acres The total area of exposed ledge surveyed is 19990 sq ft or 46 acres If you have any questions regarding the above call me directly Thank you
Sincerely
John W Myhaver Jr ^_ Field Operations Manager
Enclosure ItorLltr
Route 101 Bedford NH 03110 Phone (603) 472-4488 FAX (603) 472-9747
APPENDIX C
HEALTH AND SAFETY PHASE-OUT REPORT
HEALTH AND SAFETY PHASE-OUT REPORT SALEM ACRES SL-4 AREA
Introduction
During remediation work on SL-4 Health and Safety Monitoring was performed Cashins amp Associates Inc of Reading MA performed the following work as a subcontractor to TFCI
1) Preparation of a site-specific Health and Safety Plan (dated September 1 1995)
2) Provide a Field TechnicianIndustrial Hygienist to serve as Site Safety and Health Officer (SSHO) and to conduct air and noise monitoring
3) Provide a Certified Industrial Hygienist to review Health and Safety and to conduct site specific training (record of training included at end of Appendix C)
4) Collect 8-hour air samples for worker exposure and ambient air at the Barcelona Avenue gate Arrange for analysis of the samples and report results
5) Prepare daily and weekly Health and Safety reports
6) Prepare a Health and Safety Phase-Out Report
In general the following health and safety practices were followed
1) All workers wore hard hats safety glasses work boots gloves and hearing protection as minimum level PPE
2) When working in the exclusion zone workers wore in addition to above tyvek rubber overboots and rubber coated gloves When dust was a potential concern an industrial grade dustmist mask was also worn This level of PPE was considered Level D modified
3) Workers leaving the exclusion zone removed PPE (tyveks gloves boots and masks) in the support zone and either disposed of the items or decontaminated them
4) Workers andor visitors without 40-hour OSHA training were not permitted to enter the exclusion zone
Attached is a report prepared by Cashins amp Associates along with weekly Health and Safety Summary Reports prepared by the Field Hygienist In summary the air monitoring results indicate no levels exceeding the applicable exposure guidelines except one instance
During excavation of contaminated overburden in the northwest comer of the site an area of VOC contaminated soil was encountered Total VOCs levels measured using a PID exceeded the action level established in the Health and Safety Plan The SSHO advised TFCI to upgrade to Level C PPE in order to backfill the excavation in this area TFCI equipment operator upgraded and backfilled the area The SSHO in consultation with the Cashins CIH advised TFCI to avoid work in this area until the contaminants were characterized GEI sampled the material for waste characterization analysis and provided the results to TFCI Based on the results an action level was established by the CIH for the specific contaminants found Further PID measurements indicated levels below the new action level and work was resumed
The noise monitoring indicated that the noise level at the Barcelona Avenue gate was not exceeded Only one instance of excess noise level in the work zone was recorded (10 db(a) above the ambient noise level or 85 db(a)) Workers wore hearing protection in this instance
mdash 07171996 1601 6179444032 CASHIMS S ASSOCIATES PAGE 02
CASHINS amp Associates Inc
ItxhalrM Hy-gifnr A Invtronmtnltl Tttling
July 17 1996
Mr Jack Enos T Ford Company Inc USTenney Street Georgetown MA 01833
Dear Jack
The Site Safety and Health Officer (SSHO) from Cashing amp Associates Inc performed daily inspections of the SL-4 area Salem Acres Superfund Site between 9595 and 12195 in accordance with the Health amp Safety Plan (HSP) for the site Daily inspection logs were submitted every day No accidentsincidents were reported during the work period
In accordance with the Health amp Safety Plan the SSHO performed daily air and noise monitoring at the site during Ac project Samples were collected for metals (lead beryllium chromium arsenic) and Polynuclear Aromatic Hydrocarbons (PAHs) at the site perimeter and for workers exposure determination Coal Tar Pitch Volatiles (a benzene soluble extractables) were also used to determine the workers exposure to PAH compounds Coal Tar Pitch Volatiles (CTPV) were analyzed using OSHA 58 Method If CTPV levels oq personal samples exceed the site criteria of 02 ragm3 the sample was submitted for PAHs analysis All air samples on the site perimeter were analyzed for PAH compounds
Site monitoring air sample collection and results report were done under the supervision of a Certified Industrial Hygienist
Full shift personal worker exposure samples were collected once a week Ambient air samples were collected at the Barcelona Avenue gate about 20 feet to the west of the site gate to determine if site contaminants were migrating off site The ambient air samples were also collected once a week during the project except on rainy days and days without work with contaminated soil
All air samples were analyzed by the American Industrial Hygiene Association accredited ESA Laboratories Inc using the following methods PAHs - NIOSH 5515 Lead - NIOSH 7082 Beryllium - NIOSH 7102 Chromium - NIOSH 7024 Arsenic - NIOSH 7900 Coal Tar Pitch Volatiles - OSHA 58 All methods used are accepted by the industrial hygiene community for 8-hour exposure assessment EPA methods are usually used for ambient air measurements
CRErORTTFOmiOO
80 Mam Street bull Reading MA 01867 bull Phone- 61 7-944-4060 bull Fax 61 7-944-4082
07171996 1601 6179444032 CASHIMS amp ASSOCIATES PAGE 03
The results of air samples for metals and PAHs are presented in Table No 1
All concentrations of metals and PAHs at the site perimeter (Barcelona Avenue) and active work zones were below the OSHA Permissible Exposure Limits (PEL) and the American Conference of Governmental Industrial Hygicnists Threshold Limit Value (ACGIH TLV) Two personal samples collected on October 19 and October 23rd showed Coal Tar Pitch Volatiles (CTPV) results above OSHA PEL and AIHA TLV limits Both samples were resubmittcd to the lab for further analysis to determine if PAH compounds are present because the CTPV results were above site criteria
The results of the PAH concentrations for the personal sample on Mark Goodwin on October 19 1995 during excavation and washing trucks and for the personal sample on Ron Maker on October 23 1995 during excavating and cleaning rocks by compressed air were below OSHA PEL and ACGIH TLV limits
The SSHO performed noise monitoring according to the HSP at the exclusion zone and at the Barcelona Avenue site perimeter fence A Dupont sound level meter was used for noise monitoring The noise level in the exclusion zone during all operations except one did not exceed the on site criteria of 85 dB(a) During a short time when the air compressor had been used to clean rocks the sound level in the exclusion zone next to the air compressor did exceed 85 dB(a) Ear protection devices were worn by the workers during that operation At no time did the noise level at the Barcelona Avenue site perimeter exceed 10 dB(a) above the ambient noise level or 85 dB(a)
The SSHO performed total dust monitoring on a daily basis during the project at the site perimeter downwind of work location and at the site gate using a Miniram real time dust meter The summary of dust monitoring is presented in Table No 2 Total dust concentrations on site and off site did not exceed site criteria of 1 mgm3 and the action level of 05 nigny1
The summary of air monitoring for Volatile Organic Compounds (VOC) is presented in Table No 3 VOC concentrations in the working area did not exceed the on site criteria of 5 ppm in a breathing zone VOC concentrations on the site perimeter did not exceed real time off site criteria of 2 ppm
Five detail reports with results of air sampling were submitted during the project period
Sincerely Cashins amp Associates Inc
Evelina Vaughan Industrial Hygieflfst
CASHINS amp ASSOCIATES Inc
80 Mam Street bull Reading MA 01867 bull Phone61 7-944-4060 bull Fax 617-944-4082
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Ifxtuitral Hygltne A fnvironmtnltt Tuning
W3SXLY HBALTH amp SAFETY PLAN COMPLIANCE SUMMARY R3PORT
CLIENT T foyd C o m a n
LOCATION gal era Acres Sx^perfund Site 8L-4 Area
DATES INCLUDED IN SUMMARY
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LOCATION Salen Acres Suoerfund Site SL-4 Area
DATES INCLUDED IN SUMMARY
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Industrial Hygitnf amp CmimnmenUl Tinting
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LOCATION Salem Acres Superfund Site SL-4 Area
DATES INCLUDED IN SUMMARY
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CASHINSamp Associates Inc
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WEEKLY HEALTH 6 SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Fortjl Cqjapany
LOCATION Salem Acrlaquoa Superfund Site 9L-4 Area
DATES INCLUDED IN SUMMARY
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Industrial Hygiene amp Emironmvntal Testing
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Company
LOCATION Salem Acres Superfund Site SL-4 Area
DATES INCLUDED IN SUMMARY J_
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SERIOUS HAZARD NOTIFICATION
ISSUED TO REPRESENTING
ISSUED BY REPRESENTING CASHINS S ASSOCIATES INcT DAY DATE ISSUED O04Xmdash 1 bull-bullmdashbull f P^JT
PROJECT NAME_ SITE LOCATION
THE PURPOSE OF THE FOLLOWING STATEMENT IS TO DOCUMENT THE EXISTENCE OF A CONDITION OR CONCERN WHICH CASHINS amp ASSOCIATES INC BELIEVES WARRANTS IMMEDIATE CORRECTIVE ACTION POSSIBLE SOLUTIONS AND OR CORRECTIVE ACTIONS WILL BE INCLUDED IN THIS NOTIFICATION WHEN POSSIBLE THIS NOTIFICATION IS LIMITED TO SITUATIONS THAT REPRESENT EITHER IMMEDIATE DANGER TO LIFE OR HEALTH CONDITIONS OR PREVIOUSLY IDENTIFIED CHRONIC PROBLEMS THAT UNDERMINE OUR ABILITY TO EFFECTIVELY INSURE COMPLIANCE WITH THE REQUIREMENTS OF THE HEALTH AND SAFETY PLAN
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CISHINS amp Associates Inc
Industrial Hygirne amp Cmimnmtntal Testing
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Company
LOCATION Salem Acres Superfund Site SL-4 Area
DATES INCLUDED IN SUMMARY T
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WEEKLY HEALTH amp SA7STT PLAN COMPLIANCE SUMMARY REPORT
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LOCATION Sa^am Acras Super fund 5 jte SL-4 Area
DATES INCLUDED IN SUMMARY bull
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07161996 1650 617944408 CASHING 3 ASSOCIATES PAGE 05
CASHINSamp Associates Inc
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WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT t T Ford Coimbanv
LOCATION t Salam Acraa Suoarfund Site SL-4 Arlaquoa
DATES INCLUDED IN SUMMARYj pound mdashiffofrshy f
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CASHIMS amp ASSOCIATES PAGE 04 07161996 1658 6179444032
OVSHINSamp Associates Inc
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Company T
LOCATION Salem AcrM Suoerfund Stta 8L-4 Araa
DATES INCLUDED IN SUMMARY
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DATES INCLUDED IN SUMMARY
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CASHINS amp Associates Inc
WBBKLY HEALTH amp SAFETY FLAK COMPLIANCE SUMMARY REPORT
CLIENT T Ford Compapv
LOCATION i Sal am Acrlaquolaquo Suparfund Sita SL-4 Area
DATES INCLUDED IN SUMMARY i bull pound7 mdash
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- barcode 14732
- barcodetext SEMS Doc ID 14732
![Page 29: SALEM ACRES SUPERFUND SITE SALEM, MA ...The truck loading pa d consisted of a crushed stone are sea t up along the east sid e o f SL-4 adjacent to the access road A. row of concrete](https://reader036.vdocuments.us/reader036/viewer/2022070114/60729b840fec4e6b4d136a16/html5/thumbnails/29.jpg)
(17)
VIEW OF RESTORED SITE ON DA-1 SJDE OF FENCE - LOOKING ST
ORIGINAL IN COLOR Available at the US EPA New England Superfund Records Center
Boston MA
(18)
VIEW OF RESTORED SITE ON DA-1 SIDE OF FENCE - LOOKING WEST SL-4 ON RIGHT
APPENDIX A
ANALYTICAL RESULTS FOR
PONDED WATER
110795 1638 copy617 890 3883 TMA-WALTHAM ] 002007
PRELIMINARY REPORT UNAUDITED RESULTS
Thenno Analytical 300 Second Avenue PO Box 521 Waltham HA 02254
Attn Client Services Phone (617) 890-7200
Cashins amp Associates Order S5-11-034 55 Cambridge Street Date 110795 1522 Burlington HA 01803 Work ID Salem Acres Water
Date Received 110295 Attn Bob Cashins Date Completed
Purchase Order NA Invoice Number Client Code CASHINS
SAMPLE IDENTIFICATION
Sample Sample Number Description 01 11019S-924-01A
Sample Number 04
Sample Description
110195-9Z4-01D 02 110195-924-01B 05 110195-924-01E 03 110195-924-01C
Certified By
110795 1638 copy617 890 3883 TMA-WALTHAM 003007
PRELIMINARY REPORT UNAUDITED RESULTS
Order f S5-11-034 Thermo Analytical Page 2 110795 1522 TEST RESULTS BY SAHPLE
Test Description Volatile Organics- Aqueous Method EPA_8240 Test Code Collected 110195 02-00 Category WATER
DATE INJECTED 110695 DILUTION FACTOR 100 All results reported 1n ugL
COMPOUND RESULT DET LIMIT COMPOUND RESULT
Chloromethane U 10 Broroodi chl oromethane U Vinyl Chloride U 10 2-Chloroethyl Vinyl Ether U
Bromxnethane U 10 4-dethyl -2-pentanone U Chloroethane U 10 c1 3-1 3-Di chl oropropene U
Trichlorofluoronwthane U 50 Tol uene U Acetone 17 10 trans-1 3-Di chl oropropene LI
11-Oichloroethene U 50 11 2-Tri chl oroethane J Carbon Dlsulfide U 50 2-Hexanone U
Methyl ene Chloride U 50 Tetrachl oroethene U 12-Oichloroethene (total) U 50 D1 bromochl oromethane U
11-01 Chloroethane U 50 Chlorobenzene U Vinyl Acetate U 10 Ethyl benzene U
2-Butanone U 10 in and p-Xylene U Chloroform U 50 o-Xylene U
111-Tri Chloroethane U 50 Styrene U Carbon Tetrachlortde U 50 Broraoform U
Benzene U 50 112 2-Tat rachl oroethane U 12-01 Chloroethane U 50 1 3-01 chl orobenzene U
Trichloroethene U 50 I 4-Di chl orobenzene U 12-Dichloropropane U 50 12-01 chl orobenzene U
SURROGATE STANDARDS RESULT LEVEL X RECOVERY
12-Dichloroethane-D4 52 50 104 Toluene-08 47 50 94
l-Bromo-4-fluorobenzene 56 50 112
NOTES AND DEFINITIONS FOR THIS REPORT U =bull Undetected at stated detection limit
VOAJI
OET LIMIT
50 50
10 50 50 50 50 10
5 0 50 5 0 5 0 50 50 50 50 50 50 50 50
110795 1639 copy617 890 3883 TMA-WALTHAM copy004007
PRELIMINARY REPORT UNAUDITED RESULTS
Order t S5-11-034 Thermo Analytical Page 4 110795 1522 TEST RESULTS BY SAMPLE
ianple Description 110195-924-010 Lab No 04A Test Description RCRA Metals 1n Water Method SW846 Test Code
Collected 110195 0200 Category WATER
METAL RESULT DETECTION LIMIT METAL RESULT DETECTION LIMIT
Ag Silver U 10 As Arsenic 870 50
Ba Bar inn B69 10 Pb Lead U 50
Cd Cadmium U 50 Se Sel en1 um Z15 50
Cr Chromi um U 20 Hg Mercury U 020
NOTES AND DEFINITIONS FOR THIS REPORT All results reported in ugL U gt Undetected at stated detection limit
110795 1640 Q617 890 3883 TMA-WALTHAM 0005007
PRELIMINARY REPORT UNAUDITED RESULTS
Order S5-11-034 Thermo Analytical Page 5 110795 1522 REGULAR TEST RESULTS BY TEST
Chemical Oxygen Demand Mlnimun Maximum Method EPA600 4101
Sap Sample Description Result Units Limit Prepared Analyzed By 05A 110195-924-01E 64 bullgL 50 110395 110395 JD
Petroleum Hydrocarbons-H20 Minimum Maximum Method EPA600 4181
Samp Sample Description Result Units Limit Prepared Analyzed By 01A 110195-924-01A 108 mgL 050 110395 110395 JO
110795 1640 reg617 890 3883 TMA-WALTHAM copy006007
PRELIMINARY REPORT UNAUDITED RESULTS
Order I S5-11-034 Therm Analytical Page 6 110795 1522 TEST METHODOLOGIES
USEPA Test Methods for Evaluating Solid Wastes (SUS46 Third Edition) Method 7470 - Preparation of water for Mercury analysis
USEPA Test Methods for Evaluating Solid Vastes (SW846 Third Edition) Method 3010 - Add digestion of aqueous samples and extracts for total metals for analysis by Flame Atomic Absorption Spectroscopy or Inductively Coupled Plasma Spectroscopy
USEPA Test Methods for Evaluating Solid Vastes (SWB46 Third Edition Method 8270 mdash Gas ChroroatographyMass Spectrometry for PAHs
Volatile Organics in Water - Hazardous Substance List
SV846 Method 8240 - Modified
Test Methods for Evaluating Solid Waste SU-846 US EPA Office of Solid Waste and Emergency Response Washington 3rd Edition
Aqueous sanples are analyzed in accordance with Method 8240 using a purge and trap technique followed by 64s ChromatographyMass Spectroscopy
Quality assurance procedures for GCMS Include daily tuning and calibration of the mass spectrometer and the use of surrogate standards in each sample to monitor method performance Quantitatton is performed by the Internal standard method Analysis of blanks duplicate samples and standards are run frequently as further quality assurance procedures
USEPA Test Methods for Evaluating Solid Wastes (SW846 Third Edition) Method 3S10 mdash Separatory Funnel Liquid-Liquid Extraction
EPA-6004-79-020 - Chemical Oxygen Demand - Titrimetric Mid-Level Method 4101
EPA6004-79-020 - Petroleum Hydrocarbons 1n Water Total Recoverable Method 4181 (Spectrophotometric Infrared)
110795 1641 copy617 890 3883 TMA-WALTHAM copy007007
APPENDIX B
QUANTITY SURVEY DOCUMENTATION
TFMORAN INC Surveying - Engineering - Land Planning SoilsWetlands Mapping - Landscape Architecture
January 15 1996
Mr Jack Enos Vice President TFord Company Inc 118 Tenney Street Georgetown MA 01833
RE Survey Results - Salem Acres - SL4 Area Salem Massachusetts
Dear Jack
This letter amends the letter of December 13 1995 per our review last week
TFMoran Inc performed topographic surveys at the Salem Acres site on April 21 1994 for GEI Consultants prior to removal of material and for TFord Company on October 18 1995 after the removal of material The survey data from the original survey in 1994 was adjusted thirty feet higher to correct for a datum difference from current site datum This was due to the original reporting of the Site Benchmark (TP34) elevation as 11464 rather than 14464 which is the correct elevation
Once both topographic surfaces were on the site datum the raw cut volume was obtained by Eaglepoint (Volumes Module) Software utilizing the prismoidal method comparing the two surfaces For reference please see the attached topographic plan which superimposes the October 15 1995 contours (dark lines) over the April 21 1994 contours The volume is based on the intersection of the two surfaces Also it was noted that stock piles of material did exist on site which were not surveyed at the time
The final raw cut volume arrived at by the above methods is 12749 Cubic Yards
In November and December of 1995 the site was resurveyed to locate the area of exposed ledge at the site The results of this survey are shown on the attached topographic worksheet dated November 3 1995 and last revised January 15 1996 The results of the survey indicate the total site area to be 50860 sq ft or 117 acres The total area of exposed ledge surveyed is 19990 sq ft or 46 acres If you have any questions regarding the above call me directly Thank you
Sincerely
John W Myhaver Jr ^_ Field Operations Manager
Enclosure ItorLltr
Route 101 Bedford NH 03110 Phone (603) 472-4488 FAX (603) 472-9747
APPENDIX C
HEALTH AND SAFETY PHASE-OUT REPORT
HEALTH AND SAFETY PHASE-OUT REPORT SALEM ACRES SL-4 AREA
Introduction
During remediation work on SL-4 Health and Safety Monitoring was performed Cashins amp Associates Inc of Reading MA performed the following work as a subcontractor to TFCI
1) Preparation of a site-specific Health and Safety Plan (dated September 1 1995)
2) Provide a Field TechnicianIndustrial Hygienist to serve as Site Safety and Health Officer (SSHO) and to conduct air and noise monitoring
3) Provide a Certified Industrial Hygienist to review Health and Safety and to conduct site specific training (record of training included at end of Appendix C)
4) Collect 8-hour air samples for worker exposure and ambient air at the Barcelona Avenue gate Arrange for analysis of the samples and report results
5) Prepare daily and weekly Health and Safety reports
6) Prepare a Health and Safety Phase-Out Report
In general the following health and safety practices were followed
1) All workers wore hard hats safety glasses work boots gloves and hearing protection as minimum level PPE
2) When working in the exclusion zone workers wore in addition to above tyvek rubber overboots and rubber coated gloves When dust was a potential concern an industrial grade dustmist mask was also worn This level of PPE was considered Level D modified
3) Workers leaving the exclusion zone removed PPE (tyveks gloves boots and masks) in the support zone and either disposed of the items or decontaminated them
4) Workers andor visitors without 40-hour OSHA training were not permitted to enter the exclusion zone
Attached is a report prepared by Cashins amp Associates along with weekly Health and Safety Summary Reports prepared by the Field Hygienist In summary the air monitoring results indicate no levels exceeding the applicable exposure guidelines except one instance
During excavation of contaminated overburden in the northwest comer of the site an area of VOC contaminated soil was encountered Total VOCs levels measured using a PID exceeded the action level established in the Health and Safety Plan The SSHO advised TFCI to upgrade to Level C PPE in order to backfill the excavation in this area TFCI equipment operator upgraded and backfilled the area The SSHO in consultation with the Cashins CIH advised TFCI to avoid work in this area until the contaminants were characterized GEI sampled the material for waste characterization analysis and provided the results to TFCI Based on the results an action level was established by the CIH for the specific contaminants found Further PID measurements indicated levels below the new action level and work was resumed
The noise monitoring indicated that the noise level at the Barcelona Avenue gate was not exceeded Only one instance of excess noise level in the work zone was recorded (10 db(a) above the ambient noise level or 85 db(a)) Workers wore hearing protection in this instance
mdash 07171996 1601 6179444032 CASHIMS S ASSOCIATES PAGE 02
CASHINS amp Associates Inc
ItxhalrM Hy-gifnr A Invtronmtnltl Tttling
July 17 1996
Mr Jack Enos T Ford Company Inc USTenney Street Georgetown MA 01833
Dear Jack
The Site Safety and Health Officer (SSHO) from Cashing amp Associates Inc performed daily inspections of the SL-4 area Salem Acres Superfund Site between 9595 and 12195 in accordance with the Health amp Safety Plan (HSP) for the site Daily inspection logs were submitted every day No accidentsincidents were reported during the work period
In accordance with the Health amp Safety Plan the SSHO performed daily air and noise monitoring at the site during Ac project Samples were collected for metals (lead beryllium chromium arsenic) and Polynuclear Aromatic Hydrocarbons (PAHs) at the site perimeter and for workers exposure determination Coal Tar Pitch Volatiles (a benzene soluble extractables) were also used to determine the workers exposure to PAH compounds Coal Tar Pitch Volatiles (CTPV) were analyzed using OSHA 58 Method If CTPV levels oq personal samples exceed the site criteria of 02 ragm3 the sample was submitted for PAHs analysis All air samples on the site perimeter were analyzed for PAH compounds
Site monitoring air sample collection and results report were done under the supervision of a Certified Industrial Hygienist
Full shift personal worker exposure samples were collected once a week Ambient air samples were collected at the Barcelona Avenue gate about 20 feet to the west of the site gate to determine if site contaminants were migrating off site The ambient air samples were also collected once a week during the project except on rainy days and days without work with contaminated soil
All air samples were analyzed by the American Industrial Hygiene Association accredited ESA Laboratories Inc using the following methods PAHs - NIOSH 5515 Lead - NIOSH 7082 Beryllium - NIOSH 7102 Chromium - NIOSH 7024 Arsenic - NIOSH 7900 Coal Tar Pitch Volatiles - OSHA 58 All methods used are accepted by the industrial hygiene community for 8-hour exposure assessment EPA methods are usually used for ambient air measurements
CRErORTTFOmiOO
80 Mam Street bull Reading MA 01867 bull Phone- 61 7-944-4060 bull Fax 61 7-944-4082
07171996 1601 6179444032 CASHIMS amp ASSOCIATES PAGE 03
The results of air samples for metals and PAHs are presented in Table No 1
All concentrations of metals and PAHs at the site perimeter (Barcelona Avenue) and active work zones were below the OSHA Permissible Exposure Limits (PEL) and the American Conference of Governmental Industrial Hygicnists Threshold Limit Value (ACGIH TLV) Two personal samples collected on October 19 and October 23rd showed Coal Tar Pitch Volatiles (CTPV) results above OSHA PEL and AIHA TLV limits Both samples were resubmittcd to the lab for further analysis to determine if PAH compounds are present because the CTPV results were above site criteria
The results of the PAH concentrations for the personal sample on Mark Goodwin on October 19 1995 during excavation and washing trucks and for the personal sample on Ron Maker on October 23 1995 during excavating and cleaning rocks by compressed air were below OSHA PEL and ACGIH TLV limits
The SSHO performed noise monitoring according to the HSP at the exclusion zone and at the Barcelona Avenue site perimeter fence A Dupont sound level meter was used for noise monitoring The noise level in the exclusion zone during all operations except one did not exceed the on site criteria of 85 dB(a) During a short time when the air compressor had been used to clean rocks the sound level in the exclusion zone next to the air compressor did exceed 85 dB(a) Ear protection devices were worn by the workers during that operation At no time did the noise level at the Barcelona Avenue site perimeter exceed 10 dB(a) above the ambient noise level or 85 dB(a)
The SSHO performed total dust monitoring on a daily basis during the project at the site perimeter downwind of work location and at the site gate using a Miniram real time dust meter The summary of dust monitoring is presented in Table No 2 Total dust concentrations on site and off site did not exceed site criteria of 1 mgm3 and the action level of 05 nigny1
The summary of air monitoring for Volatile Organic Compounds (VOC) is presented in Table No 3 VOC concentrations in the working area did not exceed the on site criteria of 5 ppm in a breathing zone VOC concentrations on the site perimeter did not exceed real time off site criteria of 2 ppm
Five detail reports with results of air sampling were submitted during the project period
Sincerely Cashins amp Associates Inc
Evelina Vaughan Industrial Hygieflfst
CASHINS amp ASSOCIATES Inc
80 Mam Street bull Reading MA 01867 bull Phone61 7-944-4060 bull Fax 617-944-4082
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Ifxtuitral Hygltne A fnvironmtnltt Tuning
W3SXLY HBALTH amp SAFETY PLAN COMPLIANCE SUMMARY R3PORT
CLIENT T foyd C o m a n
LOCATION gal era Acres Sx^perfund Site 8L-4 Area
DATES INCLUDED IN SUMMARY
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WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Fprd Company
LOCATION Salen Acres Suoerfund Site SL-4 Area
DATES INCLUDED IN SUMMARY
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Industrial Hygitnf amp CmimnmenUl Tinting
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
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LOCATION Salem Acres Superfund Site SL-4 Area
DATES INCLUDED IN SUMMARY
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WEEKLY HEALTH 6 SAFETY PLAN COMPLIANCE SUMMARY REPORT
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DATES INCLUDED IN SUMMARY
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LOCATION Salem Acres Superfund Site SL-4 Area
DATES INCLUDED IN SUMMARY J_
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PROJECT NAME_ SITE LOCATION
THE PURPOSE OF THE FOLLOWING STATEMENT IS TO DOCUMENT THE EXISTENCE OF A CONDITION OR CONCERN WHICH CASHINS amp ASSOCIATES INC BELIEVES WARRANTS IMMEDIATE CORRECTIVE ACTION POSSIBLE SOLUTIONS AND OR CORRECTIVE ACTIONS WILL BE INCLUDED IN THIS NOTIFICATION WHEN POSSIBLE THIS NOTIFICATION IS LIMITED TO SITUATIONS THAT REPRESENT EITHER IMMEDIATE DANGER TO LIFE OR HEALTH CONDITIONS OR PREVIOUSLY IDENTIFIED CHRONIC PROBLEMS THAT UNDERMINE OUR ABILITY TO EFFECTIVELY INSURE COMPLIANCE WITH THE REQUIREMENTS OF THE HEALTH AND SAFETY PLAN
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Industrial Hygirne amp Cmimnmtntal Testing
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Company
LOCATION Salem Acres Superfund Site SL-4 Area
DATES INCLUDED IN SUMMARY T
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WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Company T
LOCATION Salem AcrM Suoerfund Stta 8L-4 Araa
DATES INCLUDED IN SUMMARY
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CASHINS amp Associates Inc
WBBKLY HEALTH amp SAFETY FLAK COMPLIANCE SUMMARY REPORT
CLIENT T Ford Compapv
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DATES INCLUDED IN SUMMARY i bull pound7 mdash
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- barcode 14732
- barcodetext SEMS Doc ID 14732
![Page 30: SALEM ACRES SUPERFUND SITE SALEM, MA ...The truck loading pa d consisted of a crushed stone are sea t up along the east sid e o f SL-4 adjacent to the access road A. row of concrete](https://reader036.vdocuments.us/reader036/viewer/2022070114/60729b840fec4e6b4d136a16/html5/thumbnails/30.jpg)
APPENDIX A
ANALYTICAL RESULTS FOR
PONDED WATER
110795 1638 copy617 890 3883 TMA-WALTHAM ] 002007
PRELIMINARY REPORT UNAUDITED RESULTS
Thenno Analytical 300 Second Avenue PO Box 521 Waltham HA 02254
Attn Client Services Phone (617) 890-7200
Cashins amp Associates Order S5-11-034 55 Cambridge Street Date 110795 1522 Burlington HA 01803 Work ID Salem Acres Water
Date Received 110295 Attn Bob Cashins Date Completed
Purchase Order NA Invoice Number Client Code CASHINS
SAMPLE IDENTIFICATION
Sample Sample Number Description 01 11019S-924-01A
Sample Number 04
Sample Description
110195-9Z4-01D 02 110195-924-01B 05 110195-924-01E 03 110195-924-01C
Certified By
110795 1638 copy617 890 3883 TMA-WALTHAM 003007
PRELIMINARY REPORT UNAUDITED RESULTS
Order f S5-11-034 Thermo Analytical Page 2 110795 1522 TEST RESULTS BY SAHPLE
Test Description Volatile Organics- Aqueous Method EPA_8240 Test Code Collected 110195 02-00 Category WATER
DATE INJECTED 110695 DILUTION FACTOR 100 All results reported 1n ugL
COMPOUND RESULT DET LIMIT COMPOUND RESULT
Chloromethane U 10 Broroodi chl oromethane U Vinyl Chloride U 10 2-Chloroethyl Vinyl Ether U
Bromxnethane U 10 4-dethyl -2-pentanone U Chloroethane U 10 c1 3-1 3-Di chl oropropene U
Trichlorofluoronwthane U 50 Tol uene U Acetone 17 10 trans-1 3-Di chl oropropene LI
11-Oichloroethene U 50 11 2-Tri chl oroethane J Carbon Dlsulfide U 50 2-Hexanone U
Methyl ene Chloride U 50 Tetrachl oroethene U 12-Oichloroethene (total) U 50 D1 bromochl oromethane U
11-01 Chloroethane U 50 Chlorobenzene U Vinyl Acetate U 10 Ethyl benzene U
2-Butanone U 10 in and p-Xylene U Chloroform U 50 o-Xylene U
111-Tri Chloroethane U 50 Styrene U Carbon Tetrachlortde U 50 Broraoform U
Benzene U 50 112 2-Tat rachl oroethane U 12-01 Chloroethane U 50 1 3-01 chl orobenzene U
Trichloroethene U 50 I 4-Di chl orobenzene U 12-Dichloropropane U 50 12-01 chl orobenzene U
SURROGATE STANDARDS RESULT LEVEL X RECOVERY
12-Dichloroethane-D4 52 50 104 Toluene-08 47 50 94
l-Bromo-4-fluorobenzene 56 50 112
NOTES AND DEFINITIONS FOR THIS REPORT U =bull Undetected at stated detection limit
VOAJI
OET LIMIT
50 50
10 50 50 50 50 10
5 0 50 5 0 5 0 50 50 50 50 50 50 50 50
110795 1639 copy617 890 3883 TMA-WALTHAM copy004007
PRELIMINARY REPORT UNAUDITED RESULTS
Order t S5-11-034 Thermo Analytical Page 4 110795 1522 TEST RESULTS BY SAMPLE
ianple Description 110195-924-010 Lab No 04A Test Description RCRA Metals 1n Water Method SW846 Test Code
Collected 110195 0200 Category WATER
METAL RESULT DETECTION LIMIT METAL RESULT DETECTION LIMIT
Ag Silver U 10 As Arsenic 870 50
Ba Bar inn B69 10 Pb Lead U 50
Cd Cadmium U 50 Se Sel en1 um Z15 50
Cr Chromi um U 20 Hg Mercury U 020
NOTES AND DEFINITIONS FOR THIS REPORT All results reported in ugL U gt Undetected at stated detection limit
110795 1640 Q617 890 3883 TMA-WALTHAM 0005007
PRELIMINARY REPORT UNAUDITED RESULTS
Order S5-11-034 Thermo Analytical Page 5 110795 1522 REGULAR TEST RESULTS BY TEST
Chemical Oxygen Demand Mlnimun Maximum Method EPA600 4101
Sap Sample Description Result Units Limit Prepared Analyzed By 05A 110195-924-01E 64 bullgL 50 110395 110395 JD
Petroleum Hydrocarbons-H20 Minimum Maximum Method EPA600 4181
Samp Sample Description Result Units Limit Prepared Analyzed By 01A 110195-924-01A 108 mgL 050 110395 110395 JO
110795 1640 reg617 890 3883 TMA-WALTHAM copy006007
PRELIMINARY REPORT UNAUDITED RESULTS
Order I S5-11-034 Therm Analytical Page 6 110795 1522 TEST METHODOLOGIES
USEPA Test Methods for Evaluating Solid Wastes (SUS46 Third Edition) Method 7470 - Preparation of water for Mercury analysis
USEPA Test Methods for Evaluating Solid Vastes (SW846 Third Edition) Method 3010 - Add digestion of aqueous samples and extracts for total metals for analysis by Flame Atomic Absorption Spectroscopy or Inductively Coupled Plasma Spectroscopy
USEPA Test Methods for Evaluating Solid Vastes (SWB46 Third Edition Method 8270 mdash Gas ChroroatographyMass Spectrometry for PAHs
Volatile Organics in Water - Hazardous Substance List
SV846 Method 8240 - Modified
Test Methods for Evaluating Solid Waste SU-846 US EPA Office of Solid Waste and Emergency Response Washington 3rd Edition
Aqueous sanples are analyzed in accordance with Method 8240 using a purge and trap technique followed by 64s ChromatographyMass Spectroscopy
Quality assurance procedures for GCMS Include daily tuning and calibration of the mass spectrometer and the use of surrogate standards in each sample to monitor method performance Quantitatton is performed by the Internal standard method Analysis of blanks duplicate samples and standards are run frequently as further quality assurance procedures
USEPA Test Methods for Evaluating Solid Wastes (SW846 Third Edition) Method 3S10 mdash Separatory Funnel Liquid-Liquid Extraction
EPA-6004-79-020 - Chemical Oxygen Demand - Titrimetric Mid-Level Method 4101
EPA6004-79-020 - Petroleum Hydrocarbons 1n Water Total Recoverable Method 4181 (Spectrophotometric Infrared)
110795 1641 copy617 890 3883 TMA-WALTHAM copy007007
APPENDIX B
QUANTITY SURVEY DOCUMENTATION
TFMORAN INC Surveying - Engineering - Land Planning SoilsWetlands Mapping - Landscape Architecture
January 15 1996
Mr Jack Enos Vice President TFord Company Inc 118 Tenney Street Georgetown MA 01833
RE Survey Results - Salem Acres - SL4 Area Salem Massachusetts
Dear Jack
This letter amends the letter of December 13 1995 per our review last week
TFMoran Inc performed topographic surveys at the Salem Acres site on April 21 1994 for GEI Consultants prior to removal of material and for TFord Company on October 18 1995 after the removal of material The survey data from the original survey in 1994 was adjusted thirty feet higher to correct for a datum difference from current site datum This was due to the original reporting of the Site Benchmark (TP34) elevation as 11464 rather than 14464 which is the correct elevation
Once both topographic surfaces were on the site datum the raw cut volume was obtained by Eaglepoint (Volumes Module) Software utilizing the prismoidal method comparing the two surfaces For reference please see the attached topographic plan which superimposes the October 15 1995 contours (dark lines) over the April 21 1994 contours The volume is based on the intersection of the two surfaces Also it was noted that stock piles of material did exist on site which were not surveyed at the time
The final raw cut volume arrived at by the above methods is 12749 Cubic Yards
In November and December of 1995 the site was resurveyed to locate the area of exposed ledge at the site The results of this survey are shown on the attached topographic worksheet dated November 3 1995 and last revised January 15 1996 The results of the survey indicate the total site area to be 50860 sq ft or 117 acres The total area of exposed ledge surveyed is 19990 sq ft or 46 acres If you have any questions regarding the above call me directly Thank you
Sincerely
John W Myhaver Jr ^_ Field Operations Manager
Enclosure ItorLltr
Route 101 Bedford NH 03110 Phone (603) 472-4488 FAX (603) 472-9747
APPENDIX C
HEALTH AND SAFETY PHASE-OUT REPORT
HEALTH AND SAFETY PHASE-OUT REPORT SALEM ACRES SL-4 AREA
Introduction
During remediation work on SL-4 Health and Safety Monitoring was performed Cashins amp Associates Inc of Reading MA performed the following work as a subcontractor to TFCI
1) Preparation of a site-specific Health and Safety Plan (dated September 1 1995)
2) Provide a Field TechnicianIndustrial Hygienist to serve as Site Safety and Health Officer (SSHO) and to conduct air and noise monitoring
3) Provide a Certified Industrial Hygienist to review Health and Safety and to conduct site specific training (record of training included at end of Appendix C)
4) Collect 8-hour air samples for worker exposure and ambient air at the Barcelona Avenue gate Arrange for analysis of the samples and report results
5) Prepare daily and weekly Health and Safety reports
6) Prepare a Health and Safety Phase-Out Report
In general the following health and safety practices were followed
1) All workers wore hard hats safety glasses work boots gloves and hearing protection as minimum level PPE
2) When working in the exclusion zone workers wore in addition to above tyvek rubber overboots and rubber coated gloves When dust was a potential concern an industrial grade dustmist mask was also worn This level of PPE was considered Level D modified
3) Workers leaving the exclusion zone removed PPE (tyveks gloves boots and masks) in the support zone and either disposed of the items or decontaminated them
4) Workers andor visitors without 40-hour OSHA training were not permitted to enter the exclusion zone
Attached is a report prepared by Cashins amp Associates along with weekly Health and Safety Summary Reports prepared by the Field Hygienist In summary the air monitoring results indicate no levels exceeding the applicable exposure guidelines except one instance
During excavation of contaminated overburden in the northwest comer of the site an area of VOC contaminated soil was encountered Total VOCs levels measured using a PID exceeded the action level established in the Health and Safety Plan The SSHO advised TFCI to upgrade to Level C PPE in order to backfill the excavation in this area TFCI equipment operator upgraded and backfilled the area The SSHO in consultation with the Cashins CIH advised TFCI to avoid work in this area until the contaminants were characterized GEI sampled the material for waste characterization analysis and provided the results to TFCI Based on the results an action level was established by the CIH for the specific contaminants found Further PID measurements indicated levels below the new action level and work was resumed
The noise monitoring indicated that the noise level at the Barcelona Avenue gate was not exceeded Only one instance of excess noise level in the work zone was recorded (10 db(a) above the ambient noise level or 85 db(a)) Workers wore hearing protection in this instance
mdash 07171996 1601 6179444032 CASHIMS S ASSOCIATES PAGE 02
CASHINS amp Associates Inc
ItxhalrM Hy-gifnr A Invtronmtnltl Tttling
July 17 1996
Mr Jack Enos T Ford Company Inc USTenney Street Georgetown MA 01833
Dear Jack
The Site Safety and Health Officer (SSHO) from Cashing amp Associates Inc performed daily inspections of the SL-4 area Salem Acres Superfund Site between 9595 and 12195 in accordance with the Health amp Safety Plan (HSP) for the site Daily inspection logs were submitted every day No accidentsincidents were reported during the work period
In accordance with the Health amp Safety Plan the SSHO performed daily air and noise monitoring at the site during Ac project Samples were collected for metals (lead beryllium chromium arsenic) and Polynuclear Aromatic Hydrocarbons (PAHs) at the site perimeter and for workers exposure determination Coal Tar Pitch Volatiles (a benzene soluble extractables) were also used to determine the workers exposure to PAH compounds Coal Tar Pitch Volatiles (CTPV) were analyzed using OSHA 58 Method If CTPV levels oq personal samples exceed the site criteria of 02 ragm3 the sample was submitted for PAHs analysis All air samples on the site perimeter were analyzed for PAH compounds
Site monitoring air sample collection and results report were done under the supervision of a Certified Industrial Hygienist
Full shift personal worker exposure samples were collected once a week Ambient air samples were collected at the Barcelona Avenue gate about 20 feet to the west of the site gate to determine if site contaminants were migrating off site The ambient air samples were also collected once a week during the project except on rainy days and days without work with contaminated soil
All air samples were analyzed by the American Industrial Hygiene Association accredited ESA Laboratories Inc using the following methods PAHs - NIOSH 5515 Lead - NIOSH 7082 Beryllium - NIOSH 7102 Chromium - NIOSH 7024 Arsenic - NIOSH 7900 Coal Tar Pitch Volatiles - OSHA 58 All methods used are accepted by the industrial hygiene community for 8-hour exposure assessment EPA methods are usually used for ambient air measurements
CRErORTTFOmiOO
80 Mam Street bull Reading MA 01867 bull Phone- 61 7-944-4060 bull Fax 61 7-944-4082
07171996 1601 6179444032 CASHIMS amp ASSOCIATES PAGE 03
The results of air samples for metals and PAHs are presented in Table No 1
All concentrations of metals and PAHs at the site perimeter (Barcelona Avenue) and active work zones were below the OSHA Permissible Exposure Limits (PEL) and the American Conference of Governmental Industrial Hygicnists Threshold Limit Value (ACGIH TLV) Two personal samples collected on October 19 and October 23rd showed Coal Tar Pitch Volatiles (CTPV) results above OSHA PEL and AIHA TLV limits Both samples were resubmittcd to the lab for further analysis to determine if PAH compounds are present because the CTPV results were above site criteria
The results of the PAH concentrations for the personal sample on Mark Goodwin on October 19 1995 during excavation and washing trucks and for the personal sample on Ron Maker on October 23 1995 during excavating and cleaning rocks by compressed air were below OSHA PEL and ACGIH TLV limits
The SSHO performed noise monitoring according to the HSP at the exclusion zone and at the Barcelona Avenue site perimeter fence A Dupont sound level meter was used for noise monitoring The noise level in the exclusion zone during all operations except one did not exceed the on site criteria of 85 dB(a) During a short time when the air compressor had been used to clean rocks the sound level in the exclusion zone next to the air compressor did exceed 85 dB(a) Ear protection devices were worn by the workers during that operation At no time did the noise level at the Barcelona Avenue site perimeter exceed 10 dB(a) above the ambient noise level or 85 dB(a)
The SSHO performed total dust monitoring on a daily basis during the project at the site perimeter downwind of work location and at the site gate using a Miniram real time dust meter The summary of dust monitoring is presented in Table No 2 Total dust concentrations on site and off site did not exceed site criteria of 1 mgm3 and the action level of 05 nigny1
The summary of air monitoring for Volatile Organic Compounds (VOC) is presented in Table No 3 VOC concentrations in the working area did not exceed the on site criteria of 5 ppm in a breathing zone VOC concentrations on the site perimeter did not exceed real time off site criteria of 2 ppm
Five detail reports with results of air sampling were submitted during the project period
Sincerely Cashins amp Associates Inc
Evelina Vaughan Industrial Hygieflfst
CASHINS amp ASSOCIATES Inc
80 Mam Street bull Reading MA 01867 bull Phone61 7-944-4060 bull Fax 617-944-4082
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THE PURPOSE OF THE FOLLOWING STATEMENT IS TO DOCUMENT THE EXISTENCE OF A CONDITION OR CONCERN WHICH CASHINS amp ASSOCIATES INC BELIEVES WARRANTS IMMEDIATE CORRECTIVE ACTION POSSIBLE SOLUTIONS AND OR CORRECTIVE ACTIONS WILL BE INCLUDED IN THIS NOTIFICATION WHEN POSSIBLE THIS NOTIFICATION IS LIMITED TO SITUATIONS THAT REPRESENT EITHER IMMEDIATE DANGER TO LIFE OR HEALTH CONDITIONS OR PREVIOUSLY IDENTIFIED CHRONIC PROBLEMS THAT UNDERMINE OUR ABILITY TO EFFECTIVELY INSURE COMPLIANCE WITH THE REQUIREMENTS OF THE HEALTH AND SAFETY PLAN
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CASHINS amp Associates Inc
WBBKLY HEALTH amp SAFETY FLAK COMPLIANCE SUMMARY REPORT
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- barcode 14732
- barcodetext SEMS Doc ID 14732
![Page 31: SALEM ACRES SUPERFUND SITE SALEM, MA ...The truck loading pa d consisted of a crushed stone are sea t up along the east sid e o f SL-4 adjacent to the access road A. row of concrete](https://reader036.vdocuments.us/reader036/viewer/2022070114/60729b840fec4e6b4d136a16/html5/thumbnails/31.jpg)
110795 1638 copy617 890 3883 TMA-WALTHAM ] 002007
PRELIMINARY REPORT UNAUDITED RESULTS
Thenno Analytical 300 Second Avenue PO Box 521 Waltham HA 02254
Attn Client Services Phone (617) 890-7200
Cashins amp Associates Order S5-11-034 55 Cambridge Street Date 110795 1522 Burlington HA 01803 Work ID Salem Acres Water
Date Received 110295 Attn Bob Cashins Date Completed
Purchase Order NA Invoice Number Client Code CASHINS
SAMPLE IDENTIFICATION
Sample Sample Number Description 01 11019S-924-01A
Sample Number 04
Sample Description
110195-9Z4-01D 02 110195-924-01B 05 110195-924-01E 03 110195-924-01C
Certified By
110795 1638 copy617 890 3883 TMA-WALTHAM 003007
PRELIMINARY REPORT UNAUDITED RESULTS
Order f S5-11-034 Thermo Analytical Page 2 110795 1522 TEST RESULTS BY SAHPLE
Test Description Volatile Organics- Aqueous Method EPA_8240 Test Code Collected 110195 02-00 Category WATER
DATE INJECTED 110695 DILUTION FACTOR 100 All results reported 1n ugL
COMPOUND RESULT DET LIMIT COMPOUND RESULT
Chloromethane U 10 Broroodi chl oromethane U Vinyl Chloride U 10 2-Chloroethyl Vinyl Ether U
Bromxnethane U 10 4-dethyl -2-pentanone U Chloroethane U 10 c1 3-1 3-Di chl oropropene U
Trichlorofluoronwthane U 50 Tol uene U Acetone 17 10 trans-1 3-Di chl oropropene LI
11-Oichloroethene U 50 11 2-Tri chl oroethane J Carbon Dlsulfide U 50 2-Hexanone U
Methyl ene Chloride U 50 Tetrachl oroethene U 12-Oichloroethene (total) U 50 D1 bromochl oromethane U
11-01 Chloroethane U 50 Chlorobenzene U Vinyl Acetate U 10 Ethyl benzene U
2-Butanone U 10 in and p-Xylene U Chloroform U 50 o-Xylene U
111-Tri Chloroethane U 50 Styrene U Carbon Tetrachlortde U 50 Broraoform U
Benzene U 50 112 2-Tat rachl oroethane U 12-01 Chloroethane U 50 1 3-01 chl orobenzene U
Trichloroethene U 50 I 4-Di chl orobenzene U 12-Dichloropropane U 50 12-01 chl orobenzene U
SURROGATE STANDARDS RESULT LEVEL X RECOVERY
12-Dichloroethane-D4 52 50 104 Toluene-08 47 50 94
l-Bromo-4-fluorobenzene 56 50 112
NOTES AND DEFINITIONS FOR THIS REPORT U =bull Undetected at stated detection limit
VOAJI
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50 50
10 50 50 50 50 10
5 0 50 5 0 5 0 50 50 50 50 50 50 50 50
110795 1639 copy617 890 3883 TMA-WALTHAM copy004007
PRELIMINARY REPORT UNAUDITED RESULTS
Order t S5-11-034 Thermo Analytical Page 4 110795 1522 TEST RESULTS BY SAMPLE
ianple Description 110195-924-010 Lab No 04A Test Description RCRA Metals 1n Water Method SW846 Test Code
Collected 110195 0200 Category WATER
METAL RESULT DETECTION LIMIT METAL RESULT DETECTION LIMIT
Ag Silver U 10 As Arsenic 870 50
Ba Bar inn B69 10 Pb Lead U 50
Cd Cadmium U 50 Se Sel en1 um Z15 50
Cr Chromi um U 20 Hg Mercury U 020
NOTES AND DEFINITIONS FOR THIS REPORT All results reported in ugL U gt Undetected at stated detection limit
110795 1640 Q617 890 3883 TMA-WALTHAM 0005007
PRELIMINARY REPORT UNAUDITED RESULTS
Order S5-11-034 Thermo Analytical Page 5 110795 1522 REGULAR TEST RESULTS BY TEST
Chemical Oxygen Demand Mlnimun Maximum Method EPA600 4101
Sap Sample Description Result Units Limit Prepared Analyzed By 05A 110195-924-01E 64 bullgL 50 110395 110395 JD
Petroleum Hydrocarbons-H20 Minimum Maximum Method EPA600 4181
Samp Sample Description Result Units Limit Prepared Analyzed By 01A 110195-924-01A 108 mgL 050 110395 110395 JO
110795 1640 reg617 890 3883 TMA-WALTHAM copy006007
PRELIMINARY REPORT UNAUDITED RESULTS
Order I S5-11-034 Therm Analytical Page 6 110795 1522 TEST METHODOLOGIES
USEPA Test Methods for Evaluating Solid Wastes (SUS46 Third Edition) Method 7470 - Preparation of water for Mercury analysis
USEPA Test Methods for Evaluating Solid Vastes (SW846 Third Edition) Method 3010 - Add digestion of aqueous samples and extracts for total metals for analysis by Flame Atomic Absorption Spectroscopy or Inductively Coupled Plasma Spectroscopy
USEPA Test Methods for Evaluating Solid Vastes (SWB46 Third Edition Method 8270 mdash Gas ChroroatographyMass Spectrometry for PAHs
Volatile Organics in Water - Hazardous Substance List
SV846 Method 8240 - Modified
Test Methods for Evaluating Solid Waste SU-846 US EPA Office of Solid Waste and Emergency Response Washington 3rd Edition
Aqueous sanples are analyzed in accordance with Method 8240 using a purge and trap technique followed by 64s ChromatographyMass Spectroscopy
Quality assurance procedures for GCMS Include daily tuning and calibration of the mass spectrometer and the use of surrogate standards in each sample to monitor method performance Quantitatton is performed by the Internal standard method Analysis of blanks duplicate samples and standards are run frequently as further quality assurance procedures
USEPA Test Methods for Evaluating Solid Wastes (SW846 Third Edition) Method 3S10 mdash Separatory Funnel Liquid-Liquid Extraction
EPA-6004-79-020 - Chemical Oxygen Demand - Titrimetric Mid-Level Method 4101
EPA6004-79-020 - Petroleum Hydrocarbons 1n Water Total Recoverable Method 4181 (Spectrophotometric Infrared)
110795 1641 copy617 890 3883 TMA-WALTHAM copy007007
APPENDIX B
QUANTITY SURVEY DOCUMENTATION
TFMORAN INC Surveying - Engineering - Land Planning SoilsWetlands Mapping - Landscape Architecture
January 15 1996
Mr Jack Enos Vice President TFord Company Inc 118 Tenney Street Georgetown MA 01833
RE Survey Results - Salem Acres - SL4 Area Salem Massachusetts
Dear Jack
This letter amends the letter of December 13 1995 per our review last week
TFMoran Inc performed topographic surveys at the Salem Acres site on April 21 1994 for GEI Consultants prior to removal of material and for TFord Company on October 18 1995 after the removal of material The survey data from the original survey in 1994 was adjusted thirty feet higher to correct for a datum difference from current site datum This was due to the original reporting of the Site Benchmark (TP34) elevation as 11464 rather than 14464 which is the correct elevation
Once both topographic surfaces were on the site datum the raw cut volume was obtained by Eaglepoint (Volumes Module) Software utilizing the prismoidal method comparing the two surfaces For reference please see the attached topographic plan which superimposes the October 15 1995 contours (dark lines) over the April 21 1994 contours The volume is based on the intersection of the two surfaces Also it was noted that stock piles of material did exist on site which were not surveyed at the time
The final raw cut volume arrived at by the above methods is 12749 Cubic Yards
In November and December of 1995 the site was resurveyed to locate the area of exposed ledge at the site The results of this survey are shown on the attached topographic worksheet dated November 3 1995 and last revised January 15 1996 The results of the survey indicate the total site area to be 50860 sq ft or 117 acres The total area of exposed ledge surveyed is 19990 sq ft or 46 acres If you have any questions regarding the above call me directly Thank you
Sincerely
John W Myhaver Jr ^_ Field Operations Manager
Enclosure ItorLltr
Route 101 Bedford NH 03110 Phone (603) 472-4488 FAX (603) 472-9747
APPENDIX C
HEALTH AND SAFETY PHASE-OUT REPORT
HEALTH AND SAFETY PHASE-OUT REPORT SALEM ACRES SL-4 AREA
Introduction
During remediation work on SL-4 Health and Safety Monitoring was performed Cashins amp Associates Inc of Reading MA performed the following work as a subcontractor to TFCI
1) Preparation of a site-specific Health and Safety Plan (dated September 1 1995)
2) Provide a Field TechnicianIndustrial Hygienist to serve as Site Safety and Health Officer (SSHO) and to conduct air and noise monitoring
3) Provide a Certified Industrial Hygienist to review Health and Safety and to conduct site specific training (record of training included at end of Appendix C)
4) Collect 8-hour air samples for worker exposure and ambient air at the Barcelona Avenue gate Arrange for analysis of the samples and report results
5) Prepare daily and weekly Health and Safety reports
6) Prepare a Health and Safety Phase-Out Report
In general the following health and safety practices were followed
1) All workers wore hard hats safety glasses work boots gloves and hearing protection as minimum level PPE
2) When working in the exclusion zone workers wore in addition to above tyvek rubber overboots and rubber coated gloves When dust was a potential concern an industrial grade dustmist mask was also worn This level of PPE was considered Level D modified
3) Workers leaving the exclusion zone removed PPE (tyveks gloves boots and masks) in the support zone and either disposed of the items or decontaminated them
4) Workers andor visitors without 40-hour OSHA training were not permitted to enter the exclusion zone
Attached is a report prepared by Cashins amp Associates along with weekly Health and Safety Summary Reports prepared by the Field Hygienist In summary the air monitoring results indicate no levels exceeding the applicable exposure guidelines except one instance
During excavation of contaminated overburden in the northwest comer of the site an area of VOC contaminated soil was encountered Total VOCs levels measured using a PID exceeded the action level established in the Health and Safety Plan The SSHO advised TFCI to upgrade to Level C PPE in order to backfill the excavation in this area TFCI equipment operator upgraded and backfilled the area The SSHO in consultation with the Cashins CIH advised TFCI to avoid work in this area until the contaminants were characterized GEI sampled the material for waste characterization analysis and provided the results to TFCI Based on the results an action level was established by the CIH for the specific contaminants found Further PID measurements indicated levels below the new action level and work was resumed
The noise monitoring indicated that the noise level at the Barcelona Avenue gate was not exceeded Only one instance of excess noise level in the work zone was recorded (10 db(a) above the ambient noise level or 85 db(a)) Workers wore hearing protection in this instance
mdash 07171996 1601 6179444032 CASHIMS S ASSOCIATES PAGE 02
CASHINS amp Associates Inc
ItxhalrM Hy-gifnr A Invtronmtnltl Tttling
July 17 1996
Mr Jack Enos T Ford Company Inc USTenney Street Georgetown MA 01833
Dear Jack
The Site Safety and Health Officer (SSHO) from Cashing amp Associates Inc performed daily inspections of the SL-4 area Salem Acres Superfund Site between 9595 and 12195 in accordance with the Health amp Safety Plan (HSP) for the site Daily inspection logs were submitted every day No accidentsincidents were reported during the work period
In accordance with the Health amp Safety Plan the SSHO performed daily air and noise monitoring at the site during Ac project Samples were collected for metals (lead beryllium chromium arsenic) and Polynuclear Aromatic Hydrocarbons (PAHs) at the site perimeter and for workers exposure determination Coal Tar Pitch Volatiles (a benzene soluble extractables) were also used to determine the workers exposure to PAH compounds Coal Tar Pitch Volatiles (CTPV) were analyzed using OSHA 58 Method If CTPV levels oq personal samples exceed the site criteria of 02 ragm3 the sample was submitted for PAHs analysis All air samples on the site perimeter were analyzed for PAH compounds
Site monitoring air sample collection and results report were done under the supervision of a Certified Industrial Hygienist
Full shift personal worker exposure samples were collected once a week Ambient air samples were collected at the Barcelona Avenue gate about 20 feet to the west of the site gate to determine if site contaminants were migrating off site The ambient air samples were also collected once a week during the project except on rainy days and days without work with contaminated soil
All air samples were analyzed by the American Industrial Hygiene Association accredited ESA Laboratories Inc using the following methods PAHs - NIOSH 5515 Lead - NIOSH 7082 Beryllium - NIOSH 7102 Chromium - NIOSH 7024 Arsenic - NIOSH 7900 Coal Tar Pitch Volatiles - OSHA 58 All methods used are accepted by the industrial hygiene community for 8-hour exposure assessment EPA methods are usually used for ambient air measurements
CRErORTTFOmiOO
80 Mam Street bull Reading MA 01867 bull Phone- 61 7-944-4060 bull Fax 61 7-944-4082
07171996 1601 6179444032 CASHIMS amp ASSOCIATES PAGE 03
The results of air samples for metals and PAHs are presented in Table No 1
All concentrations of metals and PAHs at the site perimeter (Barcelona Avenue) and active work zones were below the OSHA Permissible Exposure Limits (PEL) and the American Conference of Governmental Industrial Hygicnists Threshold Limit Value (ACGIH TLV) Two personal samples collected on October 19 and October 23rd showed Coal Tar Pitch Volatiles (CTPV) results above OSHA PEL and AIHA TLV limits Both samples were resubmittcd to the lab for further analysis to determine if PAH compounds are present because the CTPV results were above site criteria
The results of the PAH concentrations for the personal sample on Mark Goodwin on October 19 1995 during excavation and washing trucks and for the personal sample on Ron Maker on October 23 1995 during excavating and cleaning rocks by compressed air were below OSHA PEL and ACGIH TLV limits
The SSHO performed noise monitoring according to the HSP at the exclusion zone and at the Barcelona Avenue site perimeter fence A Dupont sound level meter was used for noise monitoring The noise level in the exclusion zone during all operations except one did not exceed the on site criteria of 85 dB(a) During a short time when the air compressor had been used to clean rocks the sound level in the exclusion zone next to the air compressor did exceed 85 dB(a) Ear protection devices were worn by the workers during that operation At no time did the noise level at the Barcelona Avenue site perimeter exceed 10 dB(a) above the ambient noise level or 85 dB(a)
The SSHO performed total dust monitoring on a daily basis during the project at the site perimeter downwind of work location and at the site gate using a Miniram real time dust meter The summary of dust monitoring is presented in Table No 2 Total dust concentrations on site and off site did not exceed site criteria of 1 mgm3 and the action level of 05 nigny1
The summary of air monitoring for Volatile Organic Compounds (VOC) is presented in Table No 3 VOC concentrations in the working area did not exceed the on site criteria of 5 ppm in a breathing zone VOC concentrations on the site perimeter did not exceed real time off site criteria of 2 ppm
Five detail reports with results of air sampling were submitted during the project period
Sincerely Cashins amp Associates Inc
Evelina Vaughan Industrial Hygieflfst
CASHINS amp ASSOCIATES Inc
80 Mam Street bull Reading MA 01867 bull Phone61 7-944-4060 bull Fax 617-944-4082
07171996 1601 6179444082 CASHINS S ASSOCIATES PAGE 04
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CASHINS amp Associates inc
Ifxtuitral Hygltne A fnvironmtnltt Tuning
W3SXLY HBALTH amp SAFETY PLAN COMPLIANCE SUMMARY R3PORT
CLIENT T foyd C o m a n
LOCATION gal era Acres Sx^perfund Site 8L-4 Area
DATES INCLUDED IN SUMMARY
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55 CAMBRIDGE STREET bull SUITE 201 bull BURLINGTON MA 01803 laquo TEL 61 -273-9080 bull FAX 67-273-9C84
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LOCATION Salen Acres Suoerfund Site SL-4 Area
DATES INCLUDED IN SUMMARY
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WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
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LOCATION Salem Acres Superfund Site SL-4 Area
DATES INCLUDED IN SUMMARY
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LOCATION Salem Acres Superfund Site SL-4 Area
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CASHINS amp Associates Inc
WBBKLY HEALTH amp SAFETY FLAK COMPLIANCE SUMMARY REPORT
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- barcode 14732
- barcodetext SEMS Doc ID 14732
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110795 1638 copy617 890 3883 TMA-WALTHAM 003007
PRELIMINARY REPORT UNAUDITED RESULTS
Order f S5-11-034 Thermo Analytical Page 2 110795 1522 TEST RESULTS BY SAHPLE
Test Description Volatile Organics- Aqueous Method EPA_8240 Test Code Collected 110195 02-00 Category WATER
DATE INJECTED 110695 DILUTION FACTOR 100 All results reported 1n ugL
COMPOUND RESULT DET LIMIT COMPOUND RESULT
Chloromethane U 10 Broroodi chl oromethane U Vinyl Chloride U 10 2-Chloroethyl Vinyl Ether U
Bromxnethane U 10 4-dethyl -2-pentanone U Chloroethane U 10 c1 3-1 3-Di chl oropropene U
Trichlorofluoronwthane U 50 Tol uene U Acetone 17 10 trans-1 3-Di chl oropropene LI
11-Oichloroethene U 50 11 2-Tri chl oroethane J Carbon Dlsulfide U 50 2-Hexanone U
Methyl ene Chloride U 50 Tetrachl oroethene U 12-Oichloroethene (total) U 50 D1 bromochl oromethane U
11-01 Chloroethane U 50 Chlorobenzene U Vinyl Acetate U 10 Ethyl benzene U
2-Butanone U 10 in and p-Xylene U Chloroform U 50 o-Xylene U
111-Tri Chloroethane U 50 Styrene U Carbon Tetrachlortde U 50 Broraoform U
Benzene U 50 112 2-Tat rachl oroethane U 12-01 Chloroethane U 50 1 3-01 chl orobenzene U
Trichloroethene U 50 I 4-Di chl orobenzene U 12-Dichloropropane U 50 12-01 chl orobenzene U
SURROGATE STANDARDS RESULT LEVEL X RECOVERY
12-Dichloroethane-D4 52 50 104 Toluene-08 47 50 94
l-Bromo-4-fluorobenzene 56 50 112
NOTES AND DEFINITIONS FOR THIS REPORT U =bull Undetected at stated detection limit
VOAJI
OET LIMIT
50 50
10 50 50 50 50 10
5 0 50 5 0 5 0 50 50 50 50 50 50 50 50
110795 1639 copy617 890 3883 TMA-WALTHAM copy004007
PRELIMINARY REPORT UNAUDITED RESULTS
Order t S5-11-034 Thermo Analytical Page 4 110795 1522 TEST RESULTS BY SAMPLE
ianple Description 110195-924-010 Lab No 04A Test Description RCRA Metals 1n Water Method SW846 Test Code
Collected 110195 0200 Category WATER
METAL RESULT DETECTION LIMIT METAL RESULT DETECTION LIMIT
Ag Silver U 10 As Arsenic 870 50
Ba Bar inn B69 10 Pb Lead U 50
Cd Cadmium U 50 Se Sel en1 um Z15 50
Cr Chromi um U 20 Hg Mercury U 020
NOTES AND DEFINITIONS FOR THIS REPORT All results reported in ugL U gt Undetected at stated detection limit
110795 1640 Q617 890 3883 TMA-WALTHAM 0005007
PRELIMINARY REPORT UNAUDITED RESULTS
Order S5-11-034 Thermo Analytical Page 5 110795 1522 REGULAR TEST RESULTS BY TEST
Chemical Oxygen Demand Mlnimun Maximum Method EPA600 4101
Sap Sample Description Result Units Limit Prepared Analyzed By 05A 110195-924-01E 64 bullgL 50 110395 110395 JD
Petroleum Hydrocarbons-H20 Minimum Maximum Method EPA600 4181
Samp Sample Description Result Units Limit Prepared Analyzed By 01A 110195-924-01A 108 mgL 050 110395 110395 JO
110795 1640 reg617 890 3883 TMA-WALTHAM copy006007
PRELIMINARY REPORT UNAUDITED RESULTS
Order I S5-11-034 Therm Analytical Page 6 110795 1522 TEST METHODOLOGIES
USEPA Test Methods for Evaluating Solid Wastes (SUS46 Third Edition) Method 7470 - Preparation of water for Mercury analysis
USEPA Test Methods for Evaluating Solid Vastes (SW846 Third Edition) Method 3010 - Add digestion of aqueous samples and extracts for total metals for analysis by Flame Atomic Absorption Spectroscopy or Inductively Coupled Plasma Spectroscopy
USEPA Test Methods for Evaluating Solid Vastes (SWB46 Third Edition Method 8270 mdash Gas ChroroatographyMass Spectrometry for PAHs
Volatile Organics in Water - Hazardous Substance List
SV846 Method 8240 - Modified
Test Methods for Evaluating Solid Waste SU-846 US EPA Office of Solid Waste and Emergency Response Washington 3rd Edition
Aqueous sanples are analyzed in accordance with Method 8240 using a purge and trap technique followed by 64s ChromatographyMass Spectroscopy
Quality assurance procedures for GCMS Include daily tuning and calibration of the mass spectrometer and the use of surrogate standards in each sample to monitor method performance Quantitatton is performed by the Internal standard method Analysis of blanks duplicate samples and standards are run frequently as further quality assurance procedures
USEPA Test Methods for Evaluating Solid Wastes (SW846 Third Edition) Method 3S10 mdash Separatory Funnel Liquid-Liquid Extraction
EPA-6004-79-020 - Chemical Oxygen Demand - Titrimetric Mid-Level Method 4101
EPA6004-79-020 - Petroleum Hydrocarbons 1n Water Total Recoverable Method 4181 (Spectrophotometric Infrared)
110795 1641 copy617 890 3883 TMA-WALTHAM copy007007
APPENDIX B
QUANTITY SURVEY DOCUMENTATION
TFMORAN INC Surveying - Engineering - Land Planning SoilsWetlands Mapping - Landscape Architecture
January 15 1996
Mr Jack Enos Vice President TFord Company Inc 118 Tenney Street Georgetown MA 01833
RE Survey Results - Salem Acres - SL4 Area Salem Massachusetts
Dear Jack
This letter amends the letter of December 13 1995 per our review last week
TFMoran Inc performed topographic surveys at the Salem Acres site on April 21 1994 for GEI Consultants prior to removal of material and for TFord Company on October 18 1995 after the removal of material The survey data from the original survey in 1994 was adjusted thirty feet higher to correct for a datum difference from current site datum This was due to the original reporting of the Site Benchmark (TP34) elevation as 11464 rather than 14464 which is the correct elevation
Once both topographic surfaces were on the site datum the raw cut volume was obtained by Eaglepoint (Volumes Module) Software utilizing the prismoidal method comparing the two surfaces For reference please see the attached topographic plan which superimposes the October 15 1995 contours (dark lines) over the April 21 1994 contours The volume is based on the intersection of the two surfaces Also it was noted that stock piles of material did exist on site which were not surveyed at the time
The final raw cut volume arrived at by the above methods is 12749 Cubic Yards
In November and December of 1995 the site was resurveyed to locate the area of exposed ledge at the site The results of this survey are shown on the attached topographic worksheet dated November 3 1995 and last revised January 15 1996 The results of the survey indicate the total site area to be 50860 sq ft or 117 acres The total area of exposed ledge surveyed is 19990 sq ft or 46 acres If you have any questions regarding the above call me directly Thank you
Sincerely
John W Myhaver Jr ^_ Field Operations Manager
Enclosure ItorLltr
Route 101 Bedford NH 03110 Phone (603) 472-4488 FAX (603) 472-9747
APPENDIX C
HEALTH AND SAFETY PHASE-OUT REPORT
HEALTH AND SAFETY PHASE-OUT REPORT SALEM ACRES SL-4 AREA
Introduction
During remediation work on SL-4 Health and Safety Monitoring was performed Cashins amp Associates Inc of Reading MA performed the following work as a subcontractor to TFCI
1) Preparation of a site-specific Health and Safety Plan (dated September 1 1995)
2) Provide a Field TechnicianIndustrial Hygienist to serve as Site Safety and Health Officer (SSHO) and to conduct air and noise monitoring
3) Provide a Certified Industrial Hygienist to review Health and Safety and to conduct site specific training (record of training included at end of Appendix C)
4) Collect 8-hour air samples for worker exposure and ambient air at the Barcelona Avenue gate Arrange for analysis of the samples and report results
5) Prepare daily and weekly Health and Safety reports
6) Prepare a Health and Safety Phase-Out Report
In general the following health and safety practices were followed
1) All workers wore hard hats safety glasses work boots gloves and hearing protection as minimum level PPE
2) When working in the exclusion zone workers wore in addition to above tyvek rubber overboots and rubber coated gloves When dust was a potential concern an industrial grade dustmist mask was also worn This level of PPE was considered Level D modified
3) Workers leaving the exclusion zone removed PPE (tyveks gloves boots and masks) in the support zone and either disposed of the items or decontaminated them
4) Workers andor visitors without 40-hour OSHA training were not permitted to enter the exclusion zone
Attached is a report prepared by Cashins amp Associates along with weekly Health and Safety Summary Reports prepared by the Field Hygienist In summary the air monitoring results indicate no levels exceeding the applicable exposure guidelines except one instance
During excavation of contaminated overburden in the northwest comer of the site an area of VOC contaminated soil was encountered Total VOCs levels measured using a PID exceeded the action level established in the Health and Safety Plan The SSHO advised TFCI to upgrade to Level C PPE in order to backfill the excavation in this area TFCI equipment operator upgraded and backfilled the area The SSHO in consultation with the Cashins CIH advised TFCI to avoid work in this area until the contaminants were characterized GEI sampled the material for waste characterization analysis and provided the results to TFCI Based on the results an action level was established by the CIH for the specific contaminants found Further PID measurements indicated levels below the new action level and work was resumed
The noise monitoring indicated that the noise level at the Barcelona Avenue gate was not exceeded Only one instance of excess noise level in the work zone was recorded (10 db(a) above the ambient noise level or 85 db(a)) Workers wore hearing protection in this instance
mdash 07171996 1601 6179444032 CASHIMS S ASSOCIATES PAGE 02
CASHINS amp Associates Inc
ItxhalrM Hy-gifnr A Invtronmtnltl Tttling
July 17 1996
Mr Jack Enos T Ford Company Inc USTenney Street Georgetown MA 01833
Dear Jack
The Site Safety and Health Officer (SSHO) from Cashing amp Associates Inc performed daily inspections of the SL-4 area Salem Acres Superfund Site between 9595 and 12195 in accordance with the Health amp Safety Plan (HSP) for the site Daily inspection logs were submitted every day No accidentsincidents were reported during the work period
In accordance with the Health amp Safety Plan the SSHO performed daily air and noise monitoring at the site during Ac project Samples were collected for metals (lead beryllium chromium arsenic) and Polynuclear Aromatic Hydrocarbons (PAHs) at the site perimeter and for workers exposure determination Coal Tar Pitch Volatiles (a benzene soluble extractables) were also used to determine the workers exposure to PAH compounds Coal Tar Pitch Volatiles (CTPV) were analyzed using OSHA 58 Method If CTPV levels oq personal samples exceed the site criteria of 02 ragm3 the sample was submitted for PAHs analysis All air samples on the site perimeter were analyzed for PAH compounds
Site monitoring air sample collection and results report were done under the supervision of a Certified Industrial Hygienist
Full shift personal worker exposure samples were collected once a week Ambient air samples were collected at the Barcelona Avenue gate about 20 feet to the west of the site gate to determine if site contaminants were migrating off site The ambient air samples were also collected once a week during the project except on rainy days and days without work with contaminated soil
All air samples were analyzed by the American Industrial Hygiene Association accredited ESA Laboratories Inc using the following methods PAHs - NIOSH 5515 Lead - NIOSH 7082 Beryllium - NIOSH 7102 Chromium - NIOSH 7024 Arsenic - NIOSH 7900 Coal Tar Pitch Volatiles - OSHA 58 All methods used are accepted by the industrial hygiene community for 8-hour exposure assessment EPA methods are usually used for ambient air measurements
CRErORTTFOmiOO
80 Mam Street bull Reading MA 01867 bull Phone- 61 7-944-4060 bull Fax 61 7-944-4082
07171996 1601 6179444032 CASHIMS amp ASSOCIATES PAGE 03
The results of air samples for metals and PAHs are presented in Table No 1
All concentrations of metals and PAHs at the site perimeter (Barcelona Avenue) and active work zones were below the OSHA Permissible Exposure Limits (PEL) and the American Conference of Governmental Industrial Hygicnists Threshold Limit Value (ACGIH TLV) Two personal samples collected on October 19 and October 23rd showed Coal Tar Pitch Volatiles (CTPV) results above OSHA PEL and AIHA TLV limits Both samples were resubmittcd to the lab for further analysis to determine if PAH compounds are present because the CTPV results were above site criteria
The results of the PAH concentrations for the personal sample on Mark Goodwin on October 19 1995 during excavation and washing trucks and for the personal sample on Ron Maker on October 23 1995 during excavating and cleaning rocks by compressed air were below OSHA PEL and ACGIH TLV limits
The SSHO performed noise monitoring according to the HSP at the exclusion zone and at the Barcelona Avenue site perimeter fence A Dupont sound level meter was used for noise monitoring The noise level in the exclusion zone during all operations except one did not exceed the on site criteria of 85 dB(a) During a short time when the air compressor had been used to clean rocks the sound level in the exclusion zone next to the air compressor did exceed 85 dB(a) Ear protection devices were worn by the workers during that operation At no time did the noise level at the Barcelona Avenue site perimeter exceed 10 dB(a) above the ambient noise level or 85 dB(a)
The SSHO performed total dust monitoring on a daily basis during the project at the site perimeter downwind of work location and at the site gate using a Miniram real time dust meter The summary of dust monitoring is presented in Table No 2 Total dust concentrations on site and off site did not exceed site criteria of 1 mgm3 and the action level of 05 nigny1
The summary of air monitoring for Volatile Organic Compounds (VOC) is presented in Table No 3 VOC concentrations in the working area did not exceed the on site criteria of 5 ppm in a breathing zone VOC concentrations on the site perimeter did not exceed real time off site criteria of 2 ppm
Five detail reports with results of air sampling were submitted during the project period
Sincerely Cashins amp Associates Inc
Evelina Vaughan Industrial Hygieflfst
CASHINS amp ASSOCIATES Inc
80 Mam Street bull Reading MA 01867 bull Phone61 7-944-4060 bull Fax 617-944-4082
07171996 1601 6179444082 CASHINS S ASSOCIATES PAGE 04
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Ifxtuitral Hygltne A fnvironmtnltt Tuning
W3SXLY HBALTH amp SAFETY PLAN COMPLIANCE SUMMARY R3PORT
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LOCATION gal era Acres Sx^perfund Site 8L-4 Area
DATES INCLUDED IN SUMMARY
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LOCATION Salen Acres Suoerfund Site SL-4 Area
DATES INCLUDED IN SUMMARY
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Industrial Hygitnf amp CmimnmenUl Tinting
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
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LOCATION Salem Acres Superfund Site SL-4 Area
DATES INCLUDED IN SUMMARY
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LOCATION Salem Acres Superfund Site SL-4 Area
DATES INCLUDED IN SUMMARY J_
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LOCATION Salem Acres Superfund Site SL-4 Area
DATES INCLUDED IN SUMMARY T
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87161996 1650 6179444882 CASHINS amp ASSOCIATES
CASHINSamp Associates Inc
WEEKLY HEALTH amp SA7STT PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Coqpanv
LOCATION Sa^am Acras Super fund 5 jte SL-4 Area
DATES INCLUDED IN SUMMARY bull
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CASHINSamp Associates Inc
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WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT ^ mdash
CLIENT T Ford Company
LOCATION Salem Acraa Suoerfund Sita 5L-4
DATES INCLUDED IN SUMMARY bull
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SUMMARIZED BY FOR CASHINS amp ASSOCIATES INC
55 CAMBRIDGE STREET bullSUITE 201 bull BURllNCTON MA 01803 bull TEL 617-273-9080 bull FAX 617-273-9084
07161996 1650 617944408 CASHING 3 ASSOCIATES PAGE 05
CASHINSamp Associates Inc
fmimnntattl few
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT t T Ford Coimbanv
LOCATION t Salam Acraa Suoarfund Site SL-4 Arlaquoa
DATES INCLUDED IN SUMMARYj pound mdashiffofrshy f
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CASHIMS amp ASSOCIATES PAGE 04 07161996 1658 6179444032
OVSHINSamp Associates Inc
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Company T
LOCATION Salem AcrM Suoerfund Stta 8L-4 Araa
DATES INCLUDED IN SUMMARY
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SUMMARIZED BY pound FOR CASHINS amp ASSOCIATES INC
55 CAMBRIDGE STREET bull SUITE 201 bull BURUNGTON MA 01803 bull TEL 617-273-9080 bull FAX 617-273-9084
07161996 1658 6179444082 CASHIMS 3 ASSOCIATES PAGE 03
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CLIENT T Ford Company t lP ~ ff2-r
LOCATION Sal era Acraa Suplaquorfund Sj-ta 8L-4 Araa
DATES INCLUDED IN SUMMARY
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55 CAMBRIDGE STREET bull SUITE 201 bull 8URUNGTON MA 01803 bull TEL 617-273-9080 bull FAX 617-273-90W
07151996 18 fO 6179444082 CASHINS S ASSOCIATES PAGE 02
CASHINS amp Associates Inc
WBBKLY HEALTH amp SAFETY FLAK COMPLIANCE SUMMARY REPORT
CLIENT T Ford Compapv
LOCATION i Sal am Acrlaquolaquo Suparfund Sita SL-4 Area
DATES INCLUDED IN SUMMARY i bull pound7 mdash
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55 CAMBRIDGE STREET SUITE 201 bull SURtlNCTON MA 01803 TEL 617-273-9080 bull FAX 61 7-273-9084
- barcode 14732
- barcodetext SEMS Doc ID 14732
![Page 33: SALEM ACRES SUPERFUND SITE SALEM, MA ...The truck loading pa d consisted of a crushed stone are sea t up along the east sid e o f SL-4 adjacent to the access road A. row of concrete](https://reader036.vdocuments.us/reader036/viewer/2022070114/60729b840fec4e6b4d136a16/html5/thumbnails/33.jpg)
110795 1639 copy617 890 3883 TMA-WALTHAM copy004007
PRELIMINARY REPORT UNAUDITED RESULTS
Order t S5-11-034 Thermo Analytical Page 4 110795 1522 TEST RESULTS BY SAMPLE
ianple Description 110195-924-010 Lab No 04A Test Description RCRA Metals 1n Water Method SW846 Test Code
Collected 110195 0200 Category WATER
METAL RESULT DETECTION LIMIT METAL RESULT DETECTION LIMIT
Ag Silver U 10 As Arsenic 870 50
Ba Bar inn B69 10 Pb Lead U 50
Cd Cadmium U 50 Se Sel en1 um Z15 50
Cr Chromi um U 20 Hg Mercury U 020
NOTES AND DEFINITIONS FOR THIS REPORT All results reported in ugL U gt Undetected at stated detection limit
110795 1640 Q617 890 3883 TMA-WALTHAM 0005007
PRELIMINARY REPORT UNAUDITED RESULTS
Order S5-11-034 Thermo Analytical Page 5 110795 1522 REGULAR TEST RESULTS BY TEST
Chemical Oxygen Demand Mlnimun Maximum Method EPA600 4101
Sap Sample Description Result Units Limit Prepared Analyzed By 05A 110195-924-01E 64 bullgL 50 110395 110395 JD
Petroleum Hydrocarbons-H20 Minimum Maximum Method EPA600 4181
Samp Sample Description Result Units Limit Prepared Analyzed By 01A 110195-924-01A 108 mgL 050 110395 110395 JO
110795 1640 reg617 890 3883 TMA-WALTHAM copy006007
PRELIMINARY REPORT UNAUDITED RESULTS
Order I S5-11-034 Therm Analytical Page 6 110795 1522 TEST METHODOLOGIES
USEPA Test Methods for Evaluating Solid Wastes (SUS46 Third Edition) Method 7470 - Preparation of water for Mercury analysis
USEPA Test Methods for Evaluating Solid Vastes (SW846 Third Edition) Method 3010 - Add digestion of aqueous samples and extracts for total metals for analysis by Flame Atomic Absorption Spectroscopy or Inductively Coupled Plasma Spectroscopy
USEPA Test Methods for Evaluating Solid Vastes (SWB46 Third Edition Method 8270 mdash Gas ChroroatographyMass Spectrometry for PAHs
Volatile Organics in Water - Hazardous Substance List
SV846 Method 8240 - Modified
Test Methods for Evaluating Solid Waste SU-846 US EPA Office of Solid Waste and Emergency Response Washington 3rd Edition
Aqueous sanples are analyzed in accordance with Method 8240 using a purge and trap technique followed by 64s ChromatographyMass Spectroscopy
Quality assurance procedures for GCMS Include daily tuning and calibration of the mass spectrometer and the use of surrogate standards in each sample to monitor method performance Quantitatton is performed by the Internal standard method Analysis of blanks duplicate samples and standards are run frequently as further quality assurance procedures
USEPA Test Methods for Evaluating Solid Wastes (SW846 Third Edition) Method 3S10 mdash Separatory Funnel Liquid-Liquid Extraction
EPA-6004-79-020 - Chemical Oxygen Demand - Titrimetric Mid-Level Method 4101
EPA6004-79-020 - Petroleum Hydrocarbons 1n Water Total Recoverable Method 4181 (Spectrophotometric Infrared)
110795 1641 copy617 890 3883 TMA-WALTHAM copy007007
APPENDIX B
QUANTITY SURVEY DOCUMENTATION
TFMORAN INC Surveying - Engineering - Land Planning SoilsWetlands Mapping - Landscape Architecture
January 15 1996
Mr Jack Enos Vice President TFord Company Inc 118 Tenney Street Georgetown MA 01833
RE Survey Results - Salem Acres - SL4 Area Salem Massachusetts
Dear Jack
This letter amends the letter of December 13 1995 per our review last week
TFMoran Inc performed topographic surveys at the Salem Acres site on April 21 1994 for GEI Consultants prior to removal of material and for TFord Company on October 18 1995 after the removal of material The survey data from the original survey in 1994 was adjusted thirty feet higher to correct for a datum difference from current site datum This was due to the original reporting of the Site Benchmark (TP34) elevation as 11464 rather than 14464 which is the correct elevation
Once both topographic surfaces were on the site datum the raw cut volume was obtained by Eaglepoint (Volumes Module) Software utilizing the prismoidal method comparing the two surfaces For reference please see the attached topographic plan which superimposes the October 15 1995 contours (dark lines) over the April 21 1994 contours The volume is based on the intersection of the two surfaces Also it was noted that stock piles of material did exist on site which were not surveyed at the time
The final raw cut volume arrived at by the above methods is 12749 Cubic Yards
In November and December of 1995 the site was resurveyed to locate the area of exposed ledge at the site The results of this survey are shown on the attached topographic worksheet dated November 3 1995 and last revised January 15 1996 The results of the survey indicate the total site area to be 50860 sq ft or 117 acres The total area of exposed ledge surveyed is 19990 sq ft or 46 acres If you have any questions regarding the above call me directly Thank you
Sincerely
John W Myhaver Jr ^_ Field Operations Manager
Enclosure ItorLltr
Route 101 Bedford NH 03110 Phone (603) 472-4488 FAX (603) 472-9747
APPENDIX C
HEALTH AND SAFETY PHASE-OUT REPORT
HEALTH AND SAFETY PHASE-OUT REPORT SALEM ACRES SL-4 AREA
Introduction
During remediation work on SL-4 Health and Safety Monitoring was performed Cashins amp Associates Inc of Reading MA performed the following work as a subcontractor to TFCI
1) Preparation of a site-specific Health and Safety Plan (dated September 1 1995)
2) Provide a Field TechnicianIndustrial Hygienist to serve as Site Safety and Health Officer (SSHO) and to conduct air and noise monitoring
3) Provide a Certified Industrial Hygienist to review Health and Safety and to conduct site specific training (record of training included at end of Appendix C)
4) Collect 8-hour air samples for worker exposure and ambient air at the Barcelona Avenue gate Arrange for analysis of the samples and report results
5) Prepare daily and weekly Health and Safety reports
6) Prepare a Health and Safety Phase-Out Report
In general the following health and safety practices were followed
1) All workers wore hard hats safety glasses work boots gloves and hearing protection as minimum level PPE
2) When working in the exclusion zone workers wore in addition to above tyvek rubber overboots and rubber coated gloves When dust was a potential concern an industrial grade dustmist mask was also worn This level of PPE was considered Level D modified
3) Workers leaving the exclusion zone removed PPE (tyveks gloves boots and masks) in the support zone and either disposed of the items or decontaminated them
4) Workers andor visitors without 40-hour OSHA training were not permitted to enter the exclusion zone
Attached is a report prepared by Cashins amp Associates along with weekly Health and Safety Summary Reports prepared by the Field Hygienist In summary the air monitoring results indicate no levels exceeding the applicable exposure guidelines except one instance
During excavation of contaminated overburden in the northwest comer of the site an area of VOC contaminated soil was encountered Total VOCs levels measured using a PID exceeded the action level established in the Health and Safety Plan The SSHO advised TFCI to upgrade to Level C PPE in order to backfill the excavation in this area TFCI equipment operator upgraded and backfilled the area The SSHO in consultation with the Cashins CIH advised TFCI to avoid work in this area until the contaminants were characterized GEI sampled the material for waste characterization analysis and provided the results to TFCI Based on the results an action level was established by the CIH for the specific contaminants found Further PID measurements indicated levels below the new action level and work was resumed
The noise monitoring indicated that the noise level at the Barcelona Avenue gate was not exceeded Only one instance of excess noise level in the work zone was recorded (10 db(a) above the ambient noise level or 85 db(a)) Workers wore hearing protection in this instance
mdash 07171996 1601 6179444032 CASHIMS S ASSOCIATES PAGE 02
CASHINS amp Associates Inc
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July 17 1996
Mr Jack Enos T Ford Company Inc USTenney Street Georgetown MA 01833
Dear Jack
The Site Safety and Health Officer (SSHO) from Cashing amp Associates Inc performed daily inspections of the SL-4 area Salem Acres Superfund Site between 9595 and 12195 in accordance with the Health amp Safety Plan (HSP) for the site Daily inspection logs were submitted every day No accidentsincidents were reported during the work period
In accordance with the Health amp Safety Plan the SSHO performed daily air and noise monitoring at the site during Ac project Samples were collected for metals (lead beryllium chromium arsenic) and Polynuclear Aromatic Hydrocarbons (PAHs) at the site perimeter and for workers exposure determination Coal Tar Pitch Volatiles (a benzene soluble extractables) were also used to determine the workers exposure to PAH compounds Coal Tar Pitch Volatiles (CTPV) were analyzed using OSHA 58 Method If CTPV levels oq personal samples exceed the site criteria of 02 ragm3 the sample was submitted for PAHs analysis All air samples on the site perimeter were analyzed for PAH compounds
Site monitoring air sample collection and results report were done under the supervision of a Certified Industrial Hygienist
Full shift personal worker exposure samples were collected once a week Ambient air samples were collected at the Barcelona Avenue gate about 20 feet to the west of the site gate to determine if site contaminants were migrating off site The ambient air samples were also collected once a week during the project except on rainy days and days without work with contaminated soil
All air samples were analyzed by the American Industrial Hygiene Association accredited ESA Laboratories Inc using the following methods PAHs - NIOSH 5515 Lead - NIOSH 7082 Beryllium - NIOSH 7102 Chromium - NIOSH 7024 Arsenic - NIOSH 7900 Coal Tar Pitch Volatiles - OSHA 58 All methods used are accepted by the industrial hygiene community for 8-hour exposure assessment EPA methods are usually used for ambient air measurements
CRErORTTFOmiOO
80 Mam Street bull Reading MA 01867 bull Phone- 61 7-944-4060 bull Fax 61 7-944-4082
07171996 1601 6179444032 CASHIMS amp ASSOCIATES PAGE 03
The results of air samples for metals and PAHs are presented in Table No 1
All concentrations of metals and PAHs at the site perimeter (Barcelona Avenue) and active work zones were below the OSHA Permissible Exposure Limits (PEL) and the American Conference of Governmental Industrial Hygicnists Threshold Limit Value (ACGIH TLV) Two personal samples collected on October 19 and October 23rd showed Coal Tar Pitch Volatiles (CTPV) results above OSHA PEL and AIHA TLV limits Both samples were resubmittcd to the lab for further analysis to determine if PAH compounds are present because the CTPV results were above site criteria
The results of the PAH concentrations for the personal sample on Mark Goodwin on October 19 1995 during excavation and washing trucks and for the personal sample on Ron Maker on October 23 1995 during excavating and cleaning rocks by compressed air were below OSHA PEL and ACGIH TLV limits
The SSHO performed noise monitoring according to the HSP at the exclusion zone and at the Barcelona Avenue site perimeter fence A Dupont sound level meter was used for noise monitoring The noise level in the exclusion zone during all operations except one did not exceed the on site criteria of 85 dB(a) During a short time when the air compressor had been used to clean rocks the sound level in the exclusion zone next to the air compressor did exceed 85 dB(a) Ear protection devices were worn by the workers during that operation At no time did the noise level at the Barcelona Avenue site perimeter exceed 10 dB(a) above the ambient noise level or 85 dB(a)
The SSHO performed total dust monitoring on a daily basis during the project at the site perimeter downwind of work location and at the site gate using a Miniram real time dust meter The summary of dust monitoring is presented in Table No 2 Total dust concentrations on site and off site did not exceed site criteria of 1 mgm3 and the action level of 05 nigny1
The summary of air monitoring for Volatile Organic Compounds (VOC) is presented in Table No 3 VOC concentrations in the working area did not exceed the on site criteria of 5 ppm in a breathing zone VOC concentrations on the site perimeter did not exceed real time off site criteria of 2 ppm
Five detail reports with results of air sampling were submitted during the project period
Sincerely Cashins amp Associates Inc
Evelina Vaughan Industrial Hygieflfst
CASHINS amp ASSOCIATES Inc
80 Mam Street bull Reading MA 01867 bull Phone61 7-944-4060 bull Fax 617-944-4082
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Ifxtuitral Hygltne A fnvironmtnltt Tuning
W3SXLY HBALTH amp SAFETY PLAN COMPLIANCE SUMMARY R3PORT
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LOCATION gal era Acres Sx^perfund Site 8L-4 Area
DATES INCLUDED IN SUMMARY
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09111995 1023 6172739084 CASHINS ASSOCIATES PAGE 01
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LOCATION Salen Acres Suoerfund Site SL-4 Area
DATES INCLUDED IN SUMMARY
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Industrial Hygitnf amp CmimnmenUl Tinting
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Compan
LOCATION Salem Acres Superfund Site SL-4 Area
DATES INCLUDED IN SUMMARY
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WEEKLY HEALTH 6 SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Fortjl Cqjapany
LOCATION Salem Acrlaquoa Superfund Site 9L-4 Area
DATES INCLUDED IN SUMMARY
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Industrial Hygiene amp Emironmvntal Testing
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Company
LOCATION Salem Acres Superfund Site SL-4 Area
DATES INCLUDED IN SUMMARY J_
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ISSUED TO REPRESENTING
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PROJECT NAME_ SITE LOCATION
THE PURPOSE OF THE FOLLOWING STATEMENT IS TO DOCUMENT THE EXISTENCE OF A CONDITION OR CONCERN WHICH CASHINS amp ASSOCIATES INC BELIEVES WARRANTS IMMEDIATE CORRECTIVE ACTION POSSIBLE SOLUTIONS AND OR CORRECTIVE ACTIONS WILL BE INCLUDED IN THIS NOTIFICATION WHEN POSSIBLE THIS NOTIFICATION IS LIMITED TO SITUATIONS THAT REPRESENT EITHER IMMEDIATE DANGER TO LIFE OR HEALTH CONDITIONS OR PREVIOUSLY IDENTIFIED CHRONIC PROBLEMS THAT UNDERMINE OUR ABILITY TO EFFECTIVELY INSURE COMPLIANCE WITH THE REQUIREMENTS OF THE HEALTH AND SAFETY PLAN
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Industrial Hygirne amp Cmimnmtntal Testing
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Company
LOCATION Salem Acres Superfund Site SL-4 Area
DATES INCLUDED IN SUMMARY T
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07161996 1650 617944408 CASHING 3 ASSOCIATES PAGE 05
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CASHIMS amp ASSOCIATES PAGE 04 07161996 1658 6179444032
OVSHINSamp Associates Inc
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Company T
LOCATION Salem AcrM Suoerfund Stta 8L-4 Araa
DATES INCLUDED IN SUMMARY
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07151996 18 fO 6179444082 CASHINS S ASSOCIATES PAGE 02
CASHINS amp Associates Inc
WBBKLY HEALTH amp SAFETY FLAK COMPLIANCE SUMMARY REPORT
CLIENT T Ford Compapv
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- barcode 14732
- barcodetext SEMS Doc ID 14732
![Page 34: SALEM ACRES SUPERFUND SITE SALEM, MA ...The truck loading pa d consisted of a crushed stone are sea t up along the east sid e o f SL-4 adjacent to the access road A. row of concrete](https://reader036.vdocuments.us/reader036/viewer/2022070114/60729b840fec4e6b4d136a16/html5/thumbnails/34.jpg)
110795 1640 Q617 890 3883 TMA-WALTHAM 0005007
PRELIMINARY REPORT UNAUDITED RESULTS
Order S5-11-034 Thermo Analytical Page 5 110795 1522 REGULAR TEST RESULTS BY TEST
Chemical Oxygen Demand Mlnimun Maximum Method EPA600 4101
Sap Sample Description Result Units Limit Prepared Analyzed By 05A 110195-924-01E 64 bullgL 50 110395 110395 JD
Petroleum Hydrocarbons-H20 Minimum Maximum Method EPA600 4181
Samp Sample Description Result Units Limit Prepared Analyzed By 01A 110195-924-01A 108 mgL 050 110395 110395 JO
110795 1640 reg617 890 3883 TMA-WALTHAM copy006007
PRELIMINARY REPORT UNAUDITED RESULTS
Order I S5-11-034 Therm Analytical Page 6 110795 1522 TEST METHODOLOGIES
USEPA Test Methods for Evaluating Solid Wastes (SUS46 Third Edition) Method 7470 - Preparation of water for Mercury analysis
USEPA Test Methods for Evaluating Solid Vastes (SW846 Third Edition) Method 3010 - Add digestion of aqueous samples and extracts for total metals for analysis by Flame Atomic Absorption Spectroscopy or Inductively Coupled Plasma Spectroscopy
USEPA Test Methods for Evaluating Solid Vastes (SWB46 Third Edition Method 8270 mdash Gas ChroroatographyMass Spectrometry for PAHs
Volatile Organics in Water - Hazardous Substance List
SV846 Method 8240 - Modified
Test Methods for Evaluating Solid Waste SU-846 US EPA Office of Solid Waste and Emergency Response Washington 3rd Edition
Aqueous sanples are analyzed in accordance with Method 8240 using a purge and trap technique followed by 64s ChromatographyMass Spectroscopy
Quality assurance procedures for GCMS Include daily tuning and calibration of the mass spectrometer and the use of surrogate standards in each sample to monitor method performance Quantitatton is performed by the Internal standard method Analysis of blanks duplicate samples and standards are run frequently as further quality assurance procedures
USEPA Test Methods for Evaluating Solid Wastes (SW846 Third Edition) Method 3S10 mdash Separatory Funnel Liquid-Liquid Extraction
EPA-6004-79-020 - Chemical Oxygen Demand - Titrimetric Mid-Level Method 4101
EPA6004-79-020 - Petroleum Hydrocarbons 1n Water Total Recoverable Method 4181 (Spectrophotometric Infrared)
110795 1641 copy617 890 3883 TMA-WALTHAM copy007007
APPENDIX B
QUANTITY SURVEY DOCUMENTATION
TFMORAN INC Surveying - Engineering - Land Planning SoilsWetlands Mapping - Landscape Architecture
January 15 1996
Mr Jack Enos Vice President TFord Company Inc 118 Tenney Street Georgetown MA 01833
RE Survey Results - Salem Acres - SL4 Area Salem Massachusetts
Dear Jack
This letter amends the letter of December 13 1995 per our review last week
TFMoran Inc performed topographic surveys at the Salem Acres site on April 21 1994 for GEI Consultants prior to removal of material and for TFord Company on October 18 1995 after the removal of material The survey data from the original survey in 1994 was adjusted thirty feet higher to correct for a datum difference from current site datum This was due to the original reporting of the Site Benchmark (TP34) elevation as 11464 rather than 14464 which is the correct elevation
Once both topographic surfaces were on the site datum the raw cut volume was obtained by Eaglepoint (Volumes Module) Software utilizing the prismoidal method comparing the two surfaces For reference please see the attached topographic plan which superimposes the October 15 1995 contours (dark lines) over the April 21 1994 contours The volume is based on the intersection of the two surfaces Also it was noted that stock piles of material did exist on site which were not surveyed at the time
The final raw cut volume arrived at by the above methods is 12749 Cubic Yards
In November and December of 1995 the site was resurveyed to locate the area of exposed ledge at the site The results of this survey are shown on the attached topographic worksheet dated November 3 1995 and last revised January 15 1996 The results of the survey indicate the total site area to be 50860 sq ft or 117 acres The total area of exposed ledge surveyed is 19990 sq ft or 46 acres If you have any questions regarding the above call me directly Thank you
Sincerely
John W Myhaver Jr ^_ Field Operations Manager
Enclosure ItorLltr
Route 101 Bedford NH 03110 Phone (603) 472-4488 FAX (603) 472-9747
APPENDIX C
HEALTH AND SAFETY PHASE-OUT REPORT
HEALTH AND SAFETY PHASE-OUT REPORT SALEM ACRES SL-4 AREA
Introduction
During remediation work on SL-4 Health and Safety Monitoring was performed Cashins amp Associates Inc of Reading MA performed the following work as a subcontractor to TFCI
1) Preparation of a site-specific Health and Safety Plan (dated September 1 1995)
2) Provide a Field TechnicianIndustrial Hygienist to serve as Site Safety and Health Officer (SSHO) and to conduct air and noise monitoring
3) Provide a Certified Industrial Hygienist to review Health and Safety and to conduct site specific training (record of training included at end of Appendix C)
4) Collect 8-hour air samples for worker exposure and ambient air at the Barcelona Avenue gate Arrange for analysis of the samples and report results
5) Prepare daily and weekly Health and Safety reports
6) Prepare a Health and Safety Phase-Out Report
In general the following health and safety practices were followed
1) All workers wore hard hats safety glasses work boots gloves and hearing protection as minimum level PPE
2) When working in the exclusion zone workers wore in addition to above tyvek rubber overboots and rubber coated gloves When dust was a potential concern an industrial grade dustmist mask was also worn This level of PPE was considered Level D modified
3) Workers leaving the exclusion zone removed PPE (tyveks gloves boots and masks) in the support zone and either disposed of the items or decontaminated them
4) Workers andor visitors without 40-hour OSHA training were not permitted to enter the exclusion zone
Attached is a report prepared by Cashins amp Associates along with weekly Health and Safety Summary Reports prepared by the Field Hygienist In summary the air monitoring results indicate no levels exceeding the applicable exposure guidelines except one instance
During excavation of contaminated overburden in the northwest comer of the site an area of VOC contaminated soil was encountered Total VOCs levels measured using a PID exceeded the action level established in the Health and Safety Plan The SSHO advised TFCI to upgrade to Level C PPE in order to backfill the excavation in this area TFCI equipment operator upgraded and backfilled the area The SSHO in consultation with the Cashins CIH advised TFCI to avoid work in this area until the contaminants were characterized GEI sampled the material for waste characterization analysis and provided the results to TFCI Based on the results an action level was established by the CIH for the specific contaminants found Further PID measurements indicated levels below the new action level and work was resumed
The noise monitoring indicated that the noise level at the Barcelona Avenue gate was not exceeded Only one instance of excess noise level in the work zone was recorded (10 db(a) above the ambient noise level or 85 db(a)) Workers wore hearing protection in this instance
mdash 07171996 1601 6179444032 CASHIMS S ASSOCIATES PAGE 02
CASHINS amp Associates Inc
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July 17 1996
Mr Jack Enos T Ford Company Inc USTenney Street Georgetown MA 01833
Dear Jack
The Site Safety and Health Officer (SSHO) from Cashing amp Associates Inc performed daily inspections of the SL-4 area Salem Acres Superfund Site between 9595 and 12195 in accordance with the Health amp Safety Plan (HSP) for the site Daily inspection logs were submitted every day No accidentsincidents were reported during the work period
In accordance with the Health amp Safety Plan the SSHO performed daily air and noise monitoring at the site during Ac project Samples were collected for metals (lead beryllium chromium arsenic) and Polynuclear Aromatic Hydrocarbons (PAHs) at the site perimeter and for workers exposure determination Coal Tar Pitch Volatiles (a benzene soluble extractables) were also used to determine the workers exposure to PAH compounds Coal Tar Pitch Volatiles (CTPV) were analyzed using OSHA 58 Method If CTPV levels oq personal samples exceed the site criteria of 02 ragm3 the sample was submitted for PAHs analysis All air samples on the site perimeter were analyzed for PAH compounds
Site monitoring air sample collection and results report were done under the supervision of a Certified Industrial Hygienist
Full shift personal worker exposure samples were collected once a week Ambient air samples were collected at the Barcelona Avenue gate about 20 feet to the west of the site gate to determine if site contaminants were migrating off site The ambient air samples were also collected once a week during the project except on rainy days and days without work with contaminated soil
All air samples were analyzed by the American Industrial Hygiene Association accredited ESA Laboratories Inc using the following methods PAHs - NIOSH 5515 Lead - NIOSH 7082 Beryllium - NIOSH 7102 Chromium - NIOSH 7024 Arsenic - NIOSH 7900 Coal Tar Pitch Volatiles - OSHA 58 All methods used are accepted by the industrial hygiene community for 8-hour exposure assessment EPA methods are usually used for ambient air measurements
CRErORTTFOmiOO
80 Mam Street bull Reading MA 01867 bull Phone- 61 7-944-4060 bull Fax 61 7-944-4082
07171996 1601 6179444032 CASHIMS amp ASSOCIATES PAGE 03
The results of air samples for metals and PAHs are presented in Table No 1
All concentrations of metals and PAHs at the site perimeter (Barcelona Avenue) and active work zones were below the OSHA Permissible Exposure Limits (PEL) and the American Conference of Governmental Industrial Hygicnists Threshold Limit Value (ACGIH TLV) Two personal samples collected on October 19 and October 23rd showed Coal Tar Pitch Volatiles (CTPV) results above OSHA PEL and AIHA TLV limits Both samples were resubmittcd to the lab for further analysis to determine if PAH compounds are present because the CTPV results were above site criteria
The results of the PAH concentrations for the personal sample on Mark Goodwin on October 19 1995 during excavation and washing trucks and for the personal sample on Ron Maker on October 23 1995 during excavating and cleaning rocks by compressed air were below OSHA PEL and ACGIH TLV limits
The SSHO performed noise monitoring according to the HSP at the exclusion zone and at the Barcelona Avenue site perimeter fence A Dupont sound level meter was used for noise monitoring The noise level in the exclusion zone during all operations except one did not exceed the on site criteria of 85 dB(a) During a short time when the air compressor had been used to clean rocks the sound level in the exclusion zone next to the air compressor did exceed 85 dB(a) Ear protection devices were worn by the workers during that operation At no time did the noise level at the Barcelona Avenue site perimeter exceed 10 dB(a) above the ambient noise level or 85 dB(a)
The SSHO performed total dust monitoring on a daily basis during the project at the site perimeter downwind of work location and at the site gate using a Miniram real time dust meter The summary of dust monitoring is presented in Table No 2 Total dust concentrations on site and off site did not exceed site criteria of 1 mgm3 and the action level of 05 nigny1
The summary of air monitoring for Volatile Organic Compounds (VOC) is presented in Table No 3 VOC concentrations in the working area did not exceed the on site criteria of 5 ppm in a breathing zone VOC concentrations on the site perimeter did not exceed real time off site criteria of 2 ppm
Five detail reports with results of air sampling were submitted during the project period
Sincerely Cashins amp Associates Inc
Evelina Vaughan Industrial Hygieflfst
CASHINS amp ASSOCIATES Inc
80 Mam Street bull Reading MA 01867 bull Phone61 7-944-4060 bull Fax 617-944-4082
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Ifxtuitral Hygltne A fnvironmtnltt Tuning
W3SXLY HBALTH amp SAFETY PLAN COMPLIANCE SUMMARY R3PORT
CLIENT T foyd C o m a n
LOCATION gal era Acres Sx^perfund Site 8L-4 Area
DATES INCLUDED IN SUMMARY
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09111995 1023 6172739084 CASHINS ASSOCIATES PAGE 01
CASHINSamp Associates Inc
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WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Fprd Company
LOCATION Salen Acres Suoerfund Site SL-4 Area
DATES INCLUDED IN SUMMARY
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CASHINS amp Associates Inc
Industrial Hygitnf amp CmimnmenUl Tinting
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Compan
LOCATION Salem Acres Superfund Site SL-4 Area
DATES INCLUDED IN SUMMARY
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LOCATION Salam Aerag SL-4
DATES INCLUDED IN SUMMARY
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CASHINSamp Associates Inc
Intutttitl Myffcnt t InvtmnmmUt Itnl
WEEKLY HEALTH 6 SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Fortjl Cqjapany
LOCATION Salem Acrlaquoa Superfund Site 9L-4 Area
DATES INCLUDED IN SUMMARY
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Industrial Hygiene amp Emironmvntal Testing
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Company
LOCATION Salem Acres Superfund Site SL-4 Area
DATES INCLUDED IN SUMMARY J_
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ISSUED TO REPRESENTING
ISSUED BY REPRESENTING CASHINS S ASSOCIATES INcT DAY DATE ISSUED O04Xmdash 1 bull-bullmdashbull f P^JT
PROJECT NAME_ SITE LOCATION
THE PURPOSE OF THE FOLLOWING STATEMENT IS TO DOCUMENT THE EXISTENCE OF A CONDITION OR CONCERN WHICH CASHINS amp ASSOCIATES INC BELIEVES WARRANTS IMMEDIATE CORRECTIVE ACTION POSSIBLE SOLUTIONS AND OR CORRECTIVE ACTIONS WILL BE INCLUDED IN THIS NOTIFICATION WHEN POSSIBLE THIS NOTIFICATION IS LIMITED TO SITUATIONS THAT REPRESENT EITHER IMMEDIATE DANGER TO LIFE OR HEALTH CONDITIONS OR PREVIOUSLY IDENTIFIED CHRONIC PROBLEMS THAT UNDERMINE OUR ABILITY TO EFFECTIVELY INSURE COMPLIANCE WITH THE REQUIREMENTS OF THE HEALTH AND SAFETY PLAN
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Industrial Hygirne amp Cmimnmtntal Testing
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Company
LOCATION Salem Acres Superfund Site SL-4 Area
DATES INCLUDED IN SUMMARY T
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WEEKLY HEALTH amp SA7STT PLAN COMPLIANCE SUMMARY REPORT
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LOCATION Sa^am Acras Super fund 5 jte SL-4 Area
DATES INCLUDED IN SUMMARY bull
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07161996 1650 617944408 CASHING 3 ASSOCIATES PAGE 05
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LOCATION t Salam Acraa Suoarfund Site SL-4 Arlaquoa
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CASHIMS amp ASSOCIATES PAGE 04 07161996 1658 6179444032
OVSHINSamp Associates Inc
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Company T
LOCATION Salem AcrM Suoerfund Stta 8L-4 Araa
DATES INCLUDED IN SUMMARY
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LOCATION Sal era Acraa Suplaquorfund Sj-ta 8L-4 Araa
DATES INCLUDED IN SUMMARY
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07151996 18 fO 6179444082 CASHINS S ASSOCIATES PAGE 02
CASHINS amp Associates Inc
WBBKLY HEALTH amp SAFETY FLAK COMPLIANCE SUMMARY REPORT
CLIENT T Ford Compapv
LOCATION i Sal am Acrlaquolaquo Suparfund Sita SL-4 Area
DATES INCLUDED IN SUMMARY i bull pound7 mdash
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- barcode 14732
- barcodetext SEMS Doc ID 14732
![Page 35: SALEM ACRES SUPERFUND SITE SALEM, MA ...The truck loading pa d consisted of a crushed stone are sea t up along the east sid e o f SL-4 adjacent to the access road A. row of concrete](https://reader036.vdocuments.us/reader036/viewer/2022070114/60729b840fec4e6b4d136a16/html5/thumbnails/35.jpg)
110795 1640 reg617 890 3883 TMA-WALTHAM copy006007
PRELIMINARY REPORT UNAUDITED RESULTS
Order I S5-11-034 Therm Analytical Page 6 110795 1522 TEST METHODOLOGIES
USEPA Test Methods for Evaluating Solid Wastes (SUS46 Third Edition) Method 7470 - Preparation of water for Mercury analysis
USEPA Test Methods for Evaluating Solid Vastes (SW846 Third Edition) Method 3010 - Add digestion of aqueous samples and extracts for total metals for analysis by Flame Atomic Absorption Spectroscopy or Inductively Coupled Plasma Spectroscopy
USEPA Test Methods for Evaluating Solid Vastes (SWB46 Third Edition Method 8270 mdash Gas ChroroatographyMass Spectrometry for PAHs
Volatile Organics in Water - Hazardous Substance List
SV846 Method 8240 - Modified
Test Methods for Evaluating Solid Waste SU-846 US EPA Office of Solid Waste and Emergency Response Washington 3rd Edition
Aqueous sanples are analyzed in accordance with Method 8240 using a purge and trap technique followed by 64s ChromatographyMass Spectroscopy
Quality assurance procedures for GCMS Include daily tuning and calibration of the mass spectrometer and the use of surrogate standards in each sample to monitor method performance Quantitatton is performed by the Internal standard method Analysis of blanks duplicate samples and standards are run frequently as further quality assurance procedures
USEPA Test Methods for Evaluating Solid Wastes (SW846 Third Edition) Method 3S10 mdash Separatory Funnel Liquid-Liquid Extraction
EPA-6004-79-020 - Chemical Oxygen Demand - Titrimetric Mid-Level Method 4101
EPA6004-79-020 - Petroleum Hydrocarbons 1n Water Total Recoverable Method 4181 (Spectrophotometric Infrared)
110795 1641 copy617 890 3883 TMA-WALTHAM copy007007
APPENDIX B
QUANTITY SURVEY DOCUMENTATION
TFMORAN INC Surveying - Engineering - Land Planning SoilsWetlands Mapping - Landscape Architecture
January 15 1996
Mr Jack Enos Vice President TFord Company Inc 118 Tenney Street Georgetown MA 01833
RE Survey Results - Salem Acres - SL4 Area Salem Massachusetts
Dear Jack
This letter amends the letter of December 13 1995 per our review last week
TFMoran Inc performed topographic surveys at the Salem Acres site on April 21 1994 for GEI Consultants prior to removal of material and for TFord Company on October 18 1995 after the removal of material The survey data from the original survey in 1994 was adjusted thirty feet higher to correct for a datum difference from current site datum This was due to the original reporting of the Site Benchmark (TP34) elevation as 11464 rather than 14464 which is the correct elevation
Once both topographic surfaces were on the site datum the raw cut volume was obtained by Eaglepoint (Volumes Module) Software utilizing the prismoidal method comparing the two surfaces For reference please see the attached topographic plan which superimposes the October 15 1995 contours (dark lines) over the April 21 1994 contours The volume is based on the intersection of the two surfaces Also it was noted that stock piles of material did exist on site which were not surveyed at the time
The final raw cut volume arrived at by the above methods is 12749 Cubic Yards
In November and December of 1995 the site was resurveyed to locate the area of exposed ledge at the site The results of this survey are shown on the attached topographic worksheet dated November 3 1995 and last revised January 15 1996 The results of the survey indicate the total site area to be 50860 sq ft or 117 acres The total area of exposed ledge surveyed is 19990 sq ft or 46 acres If you have any questions regarding the above call me directly Thank you
Sincerely
John W Myhaver Jr ^_ Field Operations Manager
Enclosure ItorLltr
Route 101 Bedford NH 03110 Phone (603) 472-4488 FAX (603) 472-9747
APPENDIX C
HEALTH AND SAFETY PHASE-OUT REPORT
HEALTH AND SAFETY PHASE-OUT REPORT SALEM ACRES SL-4 AREA
Introduction
During remediation work on SL-4 Health and Safety Monitoring was performed Cashins amp Associates Inc of Reading MA performed the following work as a subcontractor to TFCI
1) Preparation of a site-specific Health and Safety Plan (dated September 1 1995)
2) Provide a Field TechnicianIndustrial Hygienist to serve as Site Safety and Health Officer (SSHO) and to conduct air and noise monitoring
3) Provide a Certified Industrial Hygienist to review Health and Safety and to conduct site specific training (record of training included at end of Appendix C)
4) Collect 8-hour air samples for worker exposure and ambient air at the Barcelona Avenue gate Arrange for analysis of the samples and report results
5) Prepare daily and weekly Health and Safety reports
6) Prepare a Health and Safety Phase-Out Report
In general the following health and safety practices were followed
1) All workers wore hard hats safety glasses work boots gloves and hearing protection as minimum level PPE
2) When working in the exclusion zone workers wore in addition to above tyvek rubber overboots and rubber coated gloves When dust was a potential concern an industrial grade dustmist mask was also worn This level of PPE was considered Level D modified
3) Workers leaving the exclusion zone removed PPE (tyveks gloves boots and masks) in the support zone and either disposed of the items or decontaminated them
4) Workers andor visitors without 40-hour OSHA training were not permitted to enter the exclusion zone
Attached is a report prepared by Cashins amp Associates along with weekly Health and Safety Summary Reports prepared by the Field Hygienist In summary the air monitoring results indicate no levels exceeding the applicable exposure guidelines except one instance
During excavation of contaminated overburden in the northwest comer of the site an area of VOC contaminated soil was encountered Total VOCs levels measured using a PID exceeded the action level established in the Health and Safety Plan The SSHO advised TFCI to upgrade to Level C PPE in order to backfill the excavation in this area TFCI equipment operator upgraded and backfilled the area The SSHO in consultation with the Cashins CIH advised TFCI to avoid work in this area until the contaminants were characterized GEI sampled the material for waste characterization analysis and provided the results to TFCI Based on the results an action level was established by the CIH for the specific contaminants found Further PID measurements indicated levels below the new action level and work was resumed
The noise monitoring indicated that the noise level at the Barcelona Avenue gate was not exceeded Only one instance of excess noise level in the work zone was recorded (10 db(a) above the ambient noise level or 85 db(a)) Workers wore hearing protection in this instance
mdash 07171996 1601 6179444032 CASHIMS S ASSOCIATES PAGE 02
CASHINS amp Associates Inc
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July 17 1996
Mr Jack Enos T Ford Company Inc USTenney Street Georgetown MA 01833
Dear Jack
The Site Safety and Health Officer (SSHO) from Cashing amp Associates Inc performed daily inspections of the SL-4 area Salem Acres Superfund Site between 9595 and 12195 in accordance with the Health amp Safety Plan (HSP) for the site Daily inspection logs were submitted every day No accidentsincidents were reported during the work period
In accordance with the Health amp Safety Plan the SSHO performed daily air and noise monitoring at the site during Ac project Samples were collected for metals (lead beryllium chromium arsenic) and Polynuclear Aromatic Hydrocarbons (PAHs) at the site perimeter and for workers exposure determination Coal Tar Pitch Volatiles (a benzene soluble extractables) were also used to determine the workers exposure to PAH compounds Coal Tar Pitch Volatiles (CTPV) were analyzed using OSHA 58 Method If CTPV levels oq personal samples exceed the site criteria of 02 ragm3 the sample was submitted for PAHs analysis All air samples on the site perimeter were analyzed for PAH compounds
Site monitoring air sample collection and results report were done under the supervision of a Certified Industrial Hygienist
Full shift personal worker exposure samples were collected once a week Ambient air samples were collected at the Barcelona Avenue gate about 20 feet to the west of the site gate to determine if site contaminants were migrating off site The ambient air samples were also collected once a week during the project except on rainy days and days without work with contaminated soil
All air samples were analyzed by the American Industrial Hygiene Association accredited ESA Laboratories Inc using the following methods PAHs - NIOSH 5515 Lead - NIOSH 7082 Beryllium - NIOSH 7102 Chromium - NIOSH 7024 Arsenic - NIOSH 7900 Coal Tar Pitch Volatiles - OSHA 58 All methods used are accepted by the industrial hygiene community for 8-hour exposure assessment EPA methods are usually used for ambient air measurements
CRErORTTFOmiOO
80 Mam Street bull Reading MA 01867 bull Phone- 61 7-944-4060 bull Fax 61 7-944-4082
07171996 1601 6179444032 CASHIMS amp ASSOCIATES PAGE 03
The results of air samples for metals and PAHs are presented in Table No 1
All concentrations of metals and PAHs at the site perimeter (Barcelona Avenue) and active work zones were below the OSHA Permissible Exposure Limits (PEL) and the American Conference of Governmental Industrial Hygicnists Threshold Limit Value (ACGIH TLV) Two personal samples collected on October 19 and October 23rd showed Coal Tar Pitch Volatiles (CTPV) results above OSHA PEL and AIHA TLV limits Both samples were resubmittcd to the lab for further analysis to determine if PAH compounds are present because the CTPV results were above site criteria
The results of the PAH concentrations for the personal sample on Mark Goodwin on October 19 1995 during excavation and washing trucks and for the personal sample on Ron Maker on October 23 1995 during excavating and cleaning rocks by compressed air were below OSHA PEL and ACGIH TLV limits
The SSHO performed noise monitoring according to the HSP at the exclusion zone and at the Barcelona Avenue site perimeter fence A Dupont sound level meter was used for noise monitoring The noise level in the exclusion zone during all operations except one did not exceed the on site criteria of 85 dB(a) During a short time when the air compressor had been used to clean rocks the sound level in the exclusion zone next to the air compressor did exceed 85 dB(a) Ear protection devices were worn by the workers during that operation At no time did the noise level at the Barcelona Avenue site perimeter exceed 10 dB(a) above the ambient noise level or 85 dB(a)
The SSHO performed total dust monitoring on a daily basis during the project at the site perimeter downwind of work location and at the site gate using a Miniram real time dust meter The summary of dust monitoring is presented in Table No 2 Total dust concentrations on site and off site did not exceed site criteria of 1 mgm3 and the action level of 05 nigny1
The summary of air monitoring for Volatile Organic Compounds (VOC) is presented in Table No 3 VOC concentrations in the working area did not exceed the on site criteria of 5 ppm in a breathing zone VOC concentrations on the site perimeter did not exceed real time off site criteria of 2 ppm
Five detail reports with results of air sampling were submitted during the project period
Sincerely Cashins amp Associates Inc
Evelina Vaughan Industrial Hygieflfst
CASHINS amp ASSOCIATES Inc
80 Mam Street bull Reading MA 01867 bull Phone61 7-944-4060 bull Fax 617-944-4082
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DATES INCLUDED IN SUMMARY
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LOCATION Salen Acres Suoerfund Site SL-4 Area
DATES INCLUDED IN SUMMARY
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WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
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LOCATION Salem Acres Superfund Site SL-4 Area
DATES INCLUDED IN SUMMARY
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DATES INCLUDED IN SUMMARY
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Industrial Hygirne amp Cmimnmtntal Testing
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
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LOCATION Salem Acres Superfund Site SL-4 Area
DATES INCLUDED IN SUMMARY T
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OVSHINSamp Associates Inc
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Company T
LOCATION Salem AcrM Suoerfund Stta 8L-4 Araa
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CASHINS amp Associates Inc
WBBKLY HEALTH amp SAFETY FLAK COMPLIANCE SUMMARY REPORT
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- barcode 14732
- barcodetext SEMS Doc ID 14732
![Page 36: SALEM ACRES SUPERFUND SITE SALEM, MA ...The truck loading pa d consisted of a crushed stone are sea t up along the east sid e o f SL-4 adjacent to the access road A. row of concrete](https://reader036.vdocuments.us/reader036/viewer/2022070114/60729b840fec4e6b4d136a16/html5/thumbnails/36.jpg)
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APPENDIX B
QUANTITY SURVEY DOCUMENTATION
TFMORAN INC Surveying - Engineering - Land Planning SoilsWetlands Mapping - Landscape Architecture
January 15 1996
Mr Jack Enos Vice President TFord Company Inc 118 Tenney Street Georgetown MA 01833
RE Survey Results - Salem Acres - SL4 Area Salem Massachusetts
Dear Jack
This letter amends the letter of December 13 1995 per our review last week
TFMoran Inc performed topographic surveys at the Salem Acres site on April 21 1994 for GEI Consultants prior to removal of material and for TFord Company on October 18 1995 after the removal of material The survey data from the original survey in 1994 was adjusted thirty feet higher to correct for a datum difference from current site datum This was due to the original reporting of the Site Benchmark (TP34) elevation as 11464 rather than 14464 which is the correct elevation
Once both topographic surfaces were on the site datum the raw cut volume was obtained by Eaglepoint (Volumes Module) Software utilizing the prismoidal method comparing the two surfaces For reference please see the attached topographic plan which superimposes the October 15 1995 contours (dark lines) over the April 21 1994 contours The volume is based on the intersection of the two surfaces Also it was noted that stock piles of material did exist on site which were not surveyed at the time
The final raw cut volume arrived at by the above methods is 12749 Cubic Yards
In November and December of 1995 the site was resurveyed to locate the area of exposed ledge at the site The results of this survey are shown on the attached topographic worksheet dated November 3 1995 and last revised January 15 1996 The results of the survey indicate the total site area to be 50860 sq ft or 117 acres The total area of exposed ledge surveyed is 19990 sq ft or 46 acres If you have any questions regarding the above call me directly Thank you
Sincerely
John W Myhaver Jr ^_ Field Operations Manager
Enclosure ItorLltr
Route 101 Bedford NH 03110 Phone (603) 472-4488 FAX (603) 472-9747
APPENDIX C
HEALTH AND SAFETY PHASE-OUT REPORT
HEALTH AND SAFETY PHASE-OUT REPORT SALEM ACRES SL-4 AREA
Introduction
During remediation work on SL-4 Health and Safety Monitoring was performed Cashins amp Associates Inc of Reading MA performed the following work as a subcontractor to TFCI
1) Preparation of a site-specific Health and Safety Plan (dated September 1 1995)
2) Provide a Field TechnicianIndustrial Hygienist to serve as Site Safety and Health Officer (SSHO) and to conduct air and noise monitoring
3) Provide a Certified Industrial Hygienist to review Health and Safety and to conduct site specific training (record of training included at end of Appendix C)
4) Collect 8-hour air samples for worker exposure and ambient air at the Barcelona Avenue gate Arrange for analysis of the samples and report results
5) Prepare daily and weekly Health and Safety reports
6) Prepare a Health and Safety Phase-Out Report
In general the following health and safety practices were followed
1) All workers wore hard hats safety glasses work boots gloves and hearing protection as minimum level PPE
2) When working in the exclusion zone workers wore in addition to above tyvek rubber overboots and rubber coated gloves When dust was a potential concern an industrial grade dustmist mask was also worn This level of PPE was considered Level D modified
3) Workers leaving the exclusion zone removed PPE (tyveks gloves boots and masks) in the support zone and either disposed of the items or decontaminated them
4) Workers andor visitors without 40-hour OSHA training were not permitted to enter the exclusion zone
Attached is a report prepared by Cashins amp Associates along with weekly Health and Safety Summary Reports prepared by the Field Hygienist In summary the air monitoring results indicate no levels exceeding the applicable exposure guidelines except one instance
During excavation of contaminated overburden in the northwest comer of the site an area of VOC contaminated soil was encountered Total VOCs levels measured using a PID exceeded the action level established in the Health and Safety Plan The SSHO advised TFCI to upgrade to Level C PPE in order to backfill the excavation in this area TFCI equipment operator upgraded and backfilled the area The SSHO in consultation with the Cashins CIH advised TFCI to avoid work in this area until the contaminants were characterized GEI sampled the material for waste characterization analysis and provided the results to TFCI Based on the results an action level was established by the CIH for the specific contaminants found Further PID measurements indicated levels below the new action level and work was resumed
The noise monitoring indicated that the noise level at the Barcelona Avenue gate was not exceeded Only one instance of excess noise level in the work zone was recorded (10 db(a) above the ambient noise level or 85 db(a)) Workers wore hearing protection in this instance
mdash 07171996 1601 6179444032 CASHIMS S ASSOCIATES PAGE 02
CASHINS amp Associates Inc
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July 17 1996
Mr Jack Enos T Ford Company Inc USTenney Street Georgetown MA 01833
Dear Jack
The Site Safety and Health Officer (SSHO) from Cashing amp Associates Inc performed daily inspections of the SL-4 area Salem Acres Superfund Site between 9595 and 12195 in accordance with the Health amp Safety Plan (HSP) for the site Daily inspection logs were submitted every day No accidentsincidents were reported during the work period
In accordance with the Health amp Safety Plan the SSHO performed daily air and noise monitoring at the site during Ac project Samples were collected for metals (lead beryllium chromium arsenic) and Polynuclear Aromatic Hydrocarbons (PAHs) at the site perimeter and for workers exposure determination Coal Tar Pitch Volatiles (a benzene soluble extractables) were also used to determine the workers exposure to PAH compounds Coal Tar Pitch Volatiles (CTPV) were analyzed using OSHA 58 Method If CTPV levels oq personal samples exceed the site criteria of 02 ragm3 the sample was submitted for PAHs analysis All air samples on the site perimeter were analyzed for PAH compounds
Site monitoring air sample collection and results report were done under the supervision of a Certified Industrial Hygienist
Full shift personal worker exposure samples were collected once a week Ambient air samples were collected at the Barcelona Avenue gate about 20 feet to the west of the site gate to determine if site contaminants were migrating off site The ambient air samples were also collected once a week during the project except on rainy days and days without work with contaminated soil
All air samples were analyzed by the American Industrial Hygiene Association accredited ESA Laboratories Inc using the following methods PAHs - NIOSH 5515 Lead - NIOSH 7082 Beryllium - NIOSH 7102 Chromium - NIOSH 7024 Arsenic - NIOSH 7900 Coal Tar Pitch Volatiles - OSHA 58 All methods used are accepted by the industrial hygiene community for 8-hour exposure assessment EPA methods are usually used for ambient air measurements
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80 Mam Street bull Reading MA 01867 bull Phone- 61 7-944-4060 bull Fax 61 7-944-4082
07171996 1601 6179444032 CASHIMS amp ASSOCIATES PAGE 03
The results of air samples for metals and PAHs are presented in Table No 1
All concentrations of metals and PAHs at the site perimeter (Barcelona Avenue) and active work zones were below the OSHA Permissible Exposure Limits (PEL) and the American Conference of Governmental Industrial Hygicnists Threshold Limit Value (ACGIH TLV) Two personal samples collected on October 19 and October 23rd showed Coal Tar Pitch Volatiles (CTPV) results above OSHA PEL and AIHA TLV limits Both samples were resubmittcd to the lab for further analysis to determine if PAH compounds are present because the CTPV results were above site criteria
The results of the PAH concentrations for the personal sample on Mark Goodwin on October 19 1995 during excavation and washing trucks and for the personal sample on Ron Maker on October 23 1995 during excavating and cleaning rocks by compressed air were below OSHA PEL and ACGIH TLV limits
The SSHO performed noise monitoring according to the HSP at the exclusion zone and at the Barcelona Avenue site perimeter fence A Dupont sound level meter was used for noise monitoring The noise level in the exclusion zone during all operations except one did not exceed the on site criteria of 85 dB(a) During a short time when the air compressor had been used to clean rocks the sound level in the exclusion zone next to the air compressor did exceed 85 dB(a) Ear protection devices were worn by the workers during that operation At no time did the noise level at the Barcelona Avenue site perimeter exceed 10 dB(a) above the ambient noise level or 85 dB(a)
The SSHO performed total dust monitoring on a daily basis during the project at the site perimeter downwind of work location and at the site gate using a Miniram real time dust meter The summary of dust monitoring is presented in Table No 2 Total dust concentrations on site and off site did not exceed site criteria of 1 mgm3 and the action level of 05 nigny1
The summary of air monitoring for Volatile Organic Compounds (VOC) is presented in Table No 3 VOC concentrations in the working area did not exceed the on site criteria of 5 ppm in a breathing zone VOC concentrations on the site perimeter did not exceed real time off site criteria of 2 ppm
Five detail reports with results of air sampling were submitted during the project period
Sincerely Cashins amp Associates Inc
Evelina Vaughan Industrial Hygieflfst
CASHINS amp ASSOCIATES Inc
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DATES INCLUDED IN SUMMARY
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- barcode 14732
- barcodetext SEMS Doc ID 14732
![Page 37: SALEM ACRES SUPERFUND SITE SALEM, MA ...The truck loading pa d consisted of a crushed stone are sea t up along the east sid e o f SL-4 adjacent to the access road A. row of concrete](https://reader036.vdocuments.us/reader036/viewer/2022070114/60729b840fec4e6b4d136a16/html5/thumbnails/37.jpg)
APPENDIX B
QUANTITY SURVEY DOCUMENTATION
TFMORAN INC Surveying - Engineering - Land Planning SoilsWetlands Mapping - Landscape Architecture
January 15 1996
Mr Jack Enos Vice President TFord Company Inc 118 Tenney Street Georgetown MA 01833
RE Survey Results - Salem Acres - SL4 Area Salem Massachusetts
Dear Jack
This letter amends the letter of December 13 1995 per our review last week
TFMoran Inc performed topographic surveys at the Salem Acres site on April 21 1994 for GEI Consultants prior to removal of material and for TFord Company on October 18 1995 after the removal of material The survey data from the original survey in 1994 was adjusted thirty feet higher to correct for a datum difference from current site datum This was due to the original reporting of the Site Benchmark (TP34) elevation as 11464 rather than 14464 which is the correct elevation
Once both topographic surfaces were on the site datum the raw cut volume was obtained by Eaglepoint (Volumes Module) Software utilizing the prismoidal method comparing the two surfaces For reference please see the attached topographic plan which superimposes the October 15 1995 contours (dark lines) over the April 21 1994 contours The volume is based on the intersection of the two surfaces Also it was noted that stock piles of material did exist on site which were not surveyed at the time
The final raw cut volume arrived at by the above methods is 12749 Cubic Yards
In November and December of 1995 the site was resurveyed to locate the area of exposed ledge at the site The results of this survey are shown on the attached topographic worksheet dated November 3 1995 and last revised January 15 1996 The results of the survey indicate the total site area to be 50860 sq ft or 117 acres The total area of exposed ledge surveyed is 19990 sq ft or 46 acres If you have any questions regarding the above call me directly Thank you
Sincerely
John W Myhaver Jr ^_ Field Operations Manager
Enclosure ItorLltr
Route 101 Bedford NH 03110 Phone (603) 472-4488 FAX (603) 472-9747
APPENDIX C
HEALTH AND SAFETY PHASE-OUT REPORT
HEALTH AND SAFETY PHASE-OUT REPORT SALEM ACRES SL-4 AREA
Introduction
During remediation work on SL-4 Health and Safety Monitoring was performed Cashins amp Associates Inc of Reading MA performed the following work as a subcontractor to TFCI
1) Preparation of a site-specific Health and Safety Plan (dated September 1 1995)
2) Provide a Field TechnicianIndustrial Hygienist to serve as Site Safety and Health Officer (SSHO) and to conduct air and noise monitoring
3) Provide a Certified Industrial Hygienist to review Health and Safety and to conduct site specific training (record of training included at end of Appendix C)
4) Collect 8-hour air samples for worker exposure and ambient air at the Barcelona Avenue gate Arrange for analysis of the samples and report results
5) Prepare daily and weekly Health and Safety reports
6) Prepare a Health and Safety Phase-Out Report
In general the following health and safety practices were followed
1) All workers wore hard hats safety glasses work boots gloves and hearing protection as minimum level PPE
2) When working in the exclusion zone workers wore in addition to above tyvek rubber overboots and rubber coated gloves When dust was a potential concern an industrial grade dustmist mask was also worn This level of PPE was considered Level D modified
3) Workers leaving the exclusion zone removed PPE (tyveks gloves boots and masks) in the support zone and either disposed of the items or decontaminated them
4) Workers andor visitors without 40-hour OSHA training were not permitted to enter the exclusion zone
Attached is a report prepared by Cashins amp Associates along with weekly Health and Safety Summary Reports prepared by the Field Hygienist In summary the air monitoring results indicate no levels exceeding the applicable exposure guidelines except one instance
During excavation of contaminated overburden in the northwest comer of the site an area of VOC contaminated soil was encountered Total VOCs levels measured using a PID exceeded the action level established in the Health and Safety Plan The SSHO advised TFCI to upgrade to Level C PPE in order to backfill the excavation in this area TFCI equipment operator upgraded and backfilled the area The SSHO in consultation with the Cashins CIH advised TFCI to avoid work in this area until the contaminants were characterized GEI sampled the material for waste characterization analysis and provided the results to TFCI Based on the results an action level was established by the CIH for the specific contaminants found Further PID measurements indicated levels below the new action level and work was resumed
The noise monitoring indicated that the noise level at the Barcelona Avenue gate was not exceeded Only one instance of excess noise level in the work zone was recorded (10 db(a) above the ambient noise level or 85 db(a)) Workers wore hearing protection in this instance
mdash 07171996 1601 6179444032 CASHIMS S ASSOCIATES PAGE 02
CASHINS amp Associates Inc
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July 17 1996
Mr Jack Enos T Ford Company Inc USTenney Street Georgetown MA 01833
Dear Jack
The Site Safety and Health Officer (SSHO) from Cashing amp Associates Inc performed daily inspections of the SL-4 area Salem Acres Superfund Site between 9595 and 12195 in accordance with the Health amp Safety Plan (HSP) for the site Daily inspection logs were submitted every day No accidentsincidents were reported during the work period
In accordance with the Health amp Safety Plan the SSHO performed daily air and noise monitoring at the site during Ac project Samples were collected for metals (lead beryllium chromium arsenic) and Polynuclear Aromatic Hydrocarbons (PAHs) at the site perimeter and for workers exposure determination Coal Tar Pitch Volatiles (a benzene soluble extractables) were also used to determine the workers exposure to PAH compounds Coal Tar Pitch Volatiles (CTPV) were analyzed using OSHA 58 Method If CTPV levels oq personal samples exceed the site criteria of 02 ragm3 the sample was submitted for PAHs analysis All air samples on the site perimeter were analyzed for PAH compounds
Site monitoring air sample collection and results report were done under the supervision of a Certified Industrial Hygienist
Full shift personal worker exposure samples were collected once a week Ambient air samples were collected at the Barcelona Avenue gate about 20 feet to the west of the site gate to determine if site contaminants were migrating off site The ambient air samples were also collected once a week during the project except on rainy days and days without work with contaminated soil
All air samples were analyzed by the American Industrial Hygiene Association accredited ESA Laboratories Inc using the following methods PAHs - NIOSH 5515 Lead - NIOSH 7082 Beryllium - NIOSH 7102 Chromium - NIOSH 7024 Arsenic - NIOSH 7900 Coal Tar Pitch Volatiles - OSHA 58 All methods used are accepted by the industrial hygiene community for 8-hour exposure assessment EPA methods are usually used for ambient air measurements
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80 Mam Street bull Reading MA 01867 bull Phone- 61 7-944-4060 bull Fax 61 7-944-4082
07171996 1601 6179444032 CASHIMS amp ASSOCIATES PAGE 03
The results of air samples for metals and PAHs are presented in Table No 1
All concentrations of metals and PAHs at the site perimeter (Barcelona Avenue) and active work zones were below the OSHA Permissible Exposure Limits (PEL) and the American Conference of Governmental Industrial Hygicnists Threshold Limit Value (ACGIH TLV) Two personal samples collected on October 19 and October 23rd showed Coal Tar Pitch Volatiles (CTPV) results above OSHA PEL and AIHA TLV limits Both samples were resubmittcd to the lab for further analysis to determine if PAH compounds are present because the CTPV results were above site criteria
The results of the PAH concentrations for the personal sample on Mark Goodwin on October 19 1995 during excavation and washing trucks and for the personal sample on Ron Maker on October 23 1995 during excavating and cleaning rocks by compressed air were below OSHA PEL and ACGIH TLV limits
The SSHO performed noise monitoring according to the HSP at the exclusion zone and at the Barcelona Avenue site perimeter fence A Dupont sound level meter was used for noise monitoring The noise level in the exclusion zone during all operations except one did not exceed the on site criteria of 85 dB(a) During a short time when the air compressor had been used to clean rocks the sound level in the exclusion zone next to the air compressor did exceed 85 dB(a) Ear protection devices were worn by the workers during that operation At no time did the noise level at the Barcelona Avenue site perimeter exceed 10 dB(a) above the ambient noise level or 85 dB(a)
The SSHO performed total dust monitoring on a daily basis during the project at the site perimeter downwind of work location and at the site gate using a Miniram real time dust meter The summary of dust monitoring is presented in Table No 2 Total dust concentrations on site and off site did not exceed site criteria of 1 mgm3 and the action level of 05 nigny1
The summary of air monitoring for Volatile Organic Compounds (VOC) is presented in Table No 3 VOC concentrations in the working area did not exceed the on site criteria of 5 ppm in a breathing zone VOC concentrations on the site perimeter did not exceed real time off site criteria of 2 ppm
Five detail reports with results of air sampling were submitted during the project period
Sincerely Cashins amp Associates Inc
Evelina Vaughan Industrial Hygieflfst
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- barcode 14732
- barcodetext SEMS Doc ID 14732
![Page 38: SALEM ACRES SUPERFUND SITE SALEM, MA ...The truck loading pa d consisted of a crushed stone are sea t up along the east sid e o f SL-4 adjacent to the access road A. row of concrete](https://reader036.vdocuments.us/reader036/viewer/2022070114/60729b840fec4e6b4d136a16/html5/thumbnails/38.jpg)
TFMORAN INC Surveying - Engineering - Land Planning SoilsWetlands Mapping - Landscape Architecture
January 15 1996
Mr Jack Enos Vice President TFord Company Inc 118 Tenney Street Georgetown MA 01833
RE Survey Results - Salem Acres - SL4 Area Salem Massachusetts
Dear Jack
This letter amends the letter of December 13 1995 per our review last week
TFMoran Inc performed topographic surveys at the Salem Acres site on April 21 1994 for GEI Consultants prior to removal of material and for TFord Company on October 18 1995 after the removal of material The survey data from the original survey in 1994 was adjusted thirty feet higher to correct for a datum difference from current site datum This was due to the original reporting of the Site Benchmark (TP34) elevation as 11464 rather than 14464 which is the correct elevation
Once both topographic surfaces were on the site datum the raw cut volume was obtained by Eaglepoint (Volumes Module) Software utilizing the prismoidal method comparing the two surfaces For reference please see the attached topographic plan which superimposes the October 15 1995 contours (dark lines) over the April 21 1994 contours The volume is based on the intersection of the two surfaces Also it was noted that stock piles of material did exist on site which were not surveyed at the time
The final raw cut volume arrived at by the above methods is 12749 Cubic Yards
In November and December of 1995 the site was resurveyed to locate the area of exposed ledge at the site The results of this survey are shown on the attached topographic worksheet dated November 3 1995 and last revised January 15 1996 The results of the survey indicate the total site area to be 50860 sq ft or 117 acres The total area of exposed ledge surveyed is 19990 sq ft or 46 acres If you have any questions regarding the above call me directly Thank you
Sincerely
John W Myhaver Jr ^_ Field Operations Manager
Enclosure ItorLltr
Route 101 Bedford NH 03110 Phone (603) 472-4488 FAX (603) 472-9747
APPENDIX C
HEALTH AND SAFETY PHASE-OUT REPORT
HEALTH AND SAFETY PHASE-OUT REPORT SALEM ACRES SL-4 AREA
Introduction
During remediation work on SL-4 Health and Safety Monitoring was performed Cashins amp Associates Inc of Reading MA performed the following work as a subcontractor to TFCI
1) Preparation of a site-specific Health and Safety Plan (dated September 1 1995)
2) Provide a Field TechnicianIndustrial Hygienist to serve as Site Safety and Health Officer (SSHO) and to conduct air and noise monitoring
3) Provide a Certified Industrial Hygienist to review Health and Safety and to conduct site specific training (record of training included at end of Appendix C)
4) Collect 8-hour air samples for worker exposure and ambient air at the Barcelona Avenue gate Arrange for analysis of the samples and report results
5) Prepare daily and weekly Health and Safety reports
6) Prepare a Health and Safety Phase-Out Report
In general the following health and safety practices were followed
1) All workers wore hard hats safety glasses work boots gloves and hearing protection as minimum level PPE
2) When working in the exclusion zone workers wore in addition to above tyvek rubber overboots and rubber coated gloves When dust was a potential concern an industrial grade dustmist mask was also worn This level of PPE was considered Level D modified
3) Workers leaving the exclusion zone removed PPE (tyveks gloves boots and masks) in the support zone and either disposed of the items or decontaminated them
4) Workers andor visitors without 40-hour OSHA training were not permitted to enter the exclusion zone
Attached is a report prepared by Cashins amp Associates along with weekly Health and Safety Summary Reports prepared by the Field Hygienist In summary the air monitoring results indicate no levels exceeding the applicable exposure guidelines except one instance
During excavation of contaminated overburden in the northwest comer of the site an area of VOC contaminated soil was encountered Total VOCs levels measured using a PID exceeded the action level established in the Health and Safety Plan The SSHO advised TFCI to upgrade to Level C PPE in order to backfill the excavation in this area TFCI equipment operator upgraded and backfilled the area The SSHO in consultation with the Cashins CIH advised TFCI to avoid work in this area until the contaminants were characterized GEI sampled the material for waste characterization analysis and provided the results to TFCI Based on the results an action level was established by the CIH for the specific contaminants found Further PID measurements indicated levels below the new action level and work was resumed
The noise monitoring indicated that the noise level at the Barcelona Avenue gate was not exceeded Only one instance of excess noise level in the work zone was recorded (10 db(a) above the ambient noise level or 85 db(a)) Workers wore hearing protection in this instance
mdash 07171996 1601 6179444032 CASHIMS S ASSOCIATES PAGE 02
CASHINS amp Associates Inc
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July 17 1996
Mr Jack Enos T Ford Company Inc USTenney Street Georgetown MA 01833
Dear Jack
The Site Safety and Health Officer (SSHO) from Cashing amp Associates Inc performed daily inspections of the SL-4 area Salem Acres Superfund Site between 9595 and 12195 in accordance with the Health amp Safety Plan (HSP) for the site Daily inspection logs were submitted every day No accidentsincidents were reported during the work period
In accordance with the Health amp Safety Plan the SSHO performed daily air and noise monitoring at the site during Ac project Samples were collected for metals (lead beryllium chromium arsenic) and Polynuclear Aromatic Hydrocarbons (PAHs) at the site perimeter and for workers exposure determination Coal Tar Pitch Volatiles (a benzene soluble extractables) were also used to determine the workers exposure to PAH compounds Coal Tar Pitch Volatiles (CTPV) were analyzed using OSHA 58 Method If CTPV levels oq personal samples exceed the site criteria of 02 ragm3 the sample was submitted for PAHs analysis All air samples on the site perimeter were analyzed for PAH compounds
Site monitoring air sample collection and results report were done under the supervision of a Certified Industrial Hygienist
Full shift personal worker exposure samples were collected once a week Ambient air samples were collected at the Barcelona Avenue gate about 20 feet to the west of the site gate to determine if site contaminants were migrating off site The ambient air samples were also collected once a week during the project except on rainy days and days without work with contaminated soil
All air samples were analyzed by the American Industrial Hygiene Association accredited ESA Laboratories Inc using the following methods PAHs - NIOSH 5515 Lead - NIOSH 7082 Beryllium - NIOSH 7102 Chromium - NIOSH 7024 Arsenic - NIOSH 7900 Coal Tar Pitch Volatiles - OSHA 58 All methods used are accepted by the industrial hygiene community for 8-hour exposure assessment EPA methods are usually used for ambient air measurements
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80 Mam Street bull Reading MA 01867 bull Phone- 61 7-944-4060 bull Fax 61 7-944-4082
07171996 1601 6179444032 CASHIMS amp ASSOCIATES PAGE 03
The results of air samples for metals and PAHs are presented in Table No 1
All concentrations of metals and PAHs at the site perimeter (Barcelona Avenue) and active work zones were below the OSHA Permissible Exposure Limits (PEL) and the American Conference of Governmental Industrial Hygicnists Threshold Limit Value (ACGIH TLV) Two personal samples collected on October 19 and October 23rd showed Coal Tar Pitch Volatiles (CTPV) results above OSHA PEL and AIHA TLV limits Both samples were resubmittcd to the lab for further analysis to determine if PAH compounds are present because the CTPV results were above site criteria
The results of the PAH concentrations for the personal sample on Mark Goodwin on October 19 1995 during excavation and washing trucks and for the personal sample on Ron Maker on October 23 1995 during excavating and cleaning rocks by compressed air were below OSHA PEL and ACGIH TLV limits
The SSHO performed noise monitoring according to the HSP at the exclusion zone and at the Barcelona Avenue site perimeter fence A Dupont sound level meter was used for noise monitoring The noise level in the exclusion zone during all operations except one did not exceed the on site criteria of 85 dB(a) During a short time when the air compressor had been used to clean rocks the sound level in the exclusion zone next to the air compressor did exceed 85 dB(a) Ear protection devices were worn by the workers during that operation At no time did the noise level at the Barcelona Avenue site perimeter exceed 10 dB(a) above the ambient noise level or 85 dB(a)
The SSHO performed total dust monitoring on a daily basis during the project at the site perimeter downwind of work location and at the site gate using a Miniram real time dust meter The summary of dust monitoring is presented in Table No 2 Total dust concentrations on site and off site did not exceed site criteria of 1 mgm3 and the action level of 05 nigny1
The summary of air monitoring for Volatile Organic Compounds (VOC) is presented in Table No 3 VOC concentrations in the working area did not exceed the on site criteria of 5 ppm in a breathing zone VOC concentrations on the site perimeter did not exceed real time off site criteria of 2 ppm
Five detail reports with results of air sampling were submitted during the project period
Sincerely Cashins amp Associates Inc
Evelina Vaughan Industrial Hygieflfst
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LOCATION Salen Acres Suoerfund Site SL-4 Area
DATES INCLUDED IN SUMMARY
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LOCATION Salem Acres Superfund Site SL-4 Area
DATES INCLUDED IN SUMMARY
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PROJECT NAME_ SITE LOCATION
THE PURPOSE OF THE FOLLOWING STATEMENT IS TO DOCUMENT THE EXISTENCE OF A CONDITION OR CONCERN WHICH CASHINS amp ASSOCIATES INC BELIEVES WARRANTS IMMEDIATE CORRECTIVE ACTION POSSIBLE SOLUTIONS AND OR CORRECTIVE ACTIONS WILL BE INCLUDED IN THIS NOTIFICATION WHEN POSSIBLE THIS NOTIFICATION IS LIMITED TO SITUATIONS THAT REPRESENT EITHER IMMEDIATE DANGER TO LIFE OR HEALTH CONDITIONS OR PREVIOUSLY IDENTIFIED CHRONIC PROBLEMS THAT UNDERMINE OUR ABILITY TO EFFECTIVELY INSURE COMPLIANCE WITH THE REQUIREMENTS OF THE HEALTH AND SAFETY PLAN
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Industrial Hygirne amp Cmimnmtntal Testing
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
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LOCATION Salem Acres Superfund Site SL-4 Area
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CASHIMS amp ASSOCIATES PAGE 04 07161996 1658 6179444032
OVSHINSamp Associates Inc
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Company T
LOCATION Salem AcrM Suoerfund Stta 8L-4 Araa
DATES INCLUDED IN SUMMARY
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CASHINS amp Associates Inc
WBBKLY HEALTH amp SAFETY FLAK COMPLIANCE SUMMARY REPORT
CLIENT T Ford Compapv
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- barcode 14732
- barcodetext SEMS Doc ID 14732
![Page 39: SALEM ACRES SUPERFUND SITE SALEM, MA ...The truck loading pa d consisted of a crushed stone are sea t up along the east sid e o f SL-4 adjacent to the access road A. row of concrete](https://reader036.vdocuments.us/reader036/viewer/2022070114/60729b840fec4e6b4d136a16/html5/thumbnails/39.jpg)
APPENDIX C
HEALTH AND SAFETY PHASE-OUT REPORT
HEALTH AND SAFETY PHASE-OUT REPORT SALEM ACRES SL-4 AREA
Introduction
During remediation work on SL-4 Health and Safety Monitoring was performed Cashins amp Associates Inc of Reading MA performed the following work as a subcontractor to TFCI
1) Preparation of a site-specific Health and Safety Plan (dated September 1 1995)
2) Provide a Field TechnicianIndustrial Hygienist to serve as Site Safety and Health Officer (SSHO) and to conduct air and noise monitoring
3) Provide a Certified Industrial Hygienist to review Health and Safety and to conduct site specific training (record of training included at end of Appendix C)
4) Collect 8-hour air samples for worker exposure and ambient air at the Barcelona Avenue gate Arrange for analysis of the samples and report results
5) Prepare daily and weekly Health and Safety reports
6) Prepare a Health and Safety Phase-Out Report
In general the following health and safety practices were followed
1) All workers wore hard hats safety glasses work boots gloves and hearing protection as minimum level PPE
2) When working in the exclusion zone workers wore in addition to above tyvek rubber overboots and rubber coated gloves When dust was a potential concern an industrial grade dustmist mask was also worn This level of PPE was considered Level D modified
3) Workers leaving the exclusion zone removed PPE (tyveks gloves boots and masks) in the support zone and either disposed of the items or decontaminated them
4) Workers andor visitors without 40-hour OSHA training were not permitted to enter the exclusion zone
Attached is a report prepared by Cashins amp Associates along with weekly Health and Safety Summary Reports prepared by the Field Hygienist In summary the air monitoring results indicate no levels exceeding the applicable exposure guidelines except one instance
During excavation of contaminated overburden in the northwest comer of the site an area of VOC contaminated soil was encountered Total VOCs levels measured using a PID exceeded the action level established in the Health and Safety Plan The SSHO advised TFCI to upgrade to Level C PPE in order to backfill the excavation in this area TFCI equipment operator upgraded and backfilled the area The SSHO in consultation with the Cashins CIH advised TFCI to avoid work in this area until the contaminants were characterized GEI sampled the material for waste characterization analysis and provided the results to TFCI Based on the results an action level was established by the CIH for the specific contaminants found Further PID measurements indicated levels below the new action level and work was resumed
The noise monitoring indicated that the noise level at the Barcelona Avenue gate was not exceeded Only one instance of excess noise level in the work zone was recorded (10 db(a) above the ambient noise level or 85 db(a)) Workers wore hearing protection in this instance
mdash 07171996 1601 6179444032 CASHIMS S ASSOCIATES PAGE 02
CASHINS amp Associates Inc
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July 17 1996
Mr Jack Enos T Ford Company Inc USTenney Street Georgetown MA 01833
Dear Jack
The Site Safety and Health Officer (SSHO) from Cashing amp Associates Inc performed daily inspections of the SL-4 area Salem Acres Superfund Site between 9595 and 12195 in accordance with the Health amp Safety Plan (HSP) for the site Daily inspection logs were submitted every day No accidentsincidents were reported during the work period
In accordance with the Health amp Safety Plan the SSHO performed daily air and noise monitoring at the site during Ac project Samples were collected for metals (lead beryllium chromium arsenic) and Polynuclear Aromatic Hydrocarbons (PAHs) at the site perimeter and for workers exposure determination Coal Tar Pitch Volatiles (a benzene soluble extractables) were also used to determine the workers exposure to PAH compounds Coal Tar Pitch Volatiles (CTPV) were analyzed using OSHA 58 Method If CTPV levels oq personal samples exceed the site criteria of 02 ragm3 the sample was submitted for PAHs analysis All air samples on the site perimeter were analyzed for PAH compounds
Site monitoring air sample collection and results report were done under the supervision of a Certified Industrial Hygienist
Full shift personal worker exposure samples were collected once a week Ambient air samples were collected at the Barcelona Avenue gate about 20 feet to the west of the site gate to determine if site contaminants were migrating off site The ambient air samples were also collected once a week during the project except on rainy days and days without work with contaminated soil
All air samples were analyzed by the American Industrial Hygiene Association accredited ESA Laboratories Inc using the following methods PAHs - NIOSH 5515 Lead - NIOSH 7082 Beryllium - NIOSH 7102 Chromium - NIOSH 7024 Arsenic - NIOSH 7900 Coal Tar Pitch Volatiles - OSHA 58 All methods used are accepted by the industrial hygiene community for 8-hour exposure assessment EPA methods are usually used for ambient air measurements
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07171996 1601 6179444032 CASHIMS amp ASSOCIATES PAGE 03
The results of air samples for metals and PAHs are presented in Table No 1
All concentrations of metals and PAHs at the site perimeter (Barcelona Avenue) and active work zones were below the OSHA Permissible Exposure Limits (PEL) and the American Conference of Governmental Industrial Hygicnists Threshold Limit Value (ACGIH TLV) Two personal samples collected on October 19 and October 23rd showed Coal Tar Pitch Volatiles (CTPV) results above OSHA PEL and AIHA TLV limits Both samples were resubmittcd to the lab for further analysis to determine if PAH compounds are present because the CTPV results were above site criteria
The results of the PAH concentrations for the personal sample on Mark Goodwin on October 19 1995 during excavation and washing trucks and for the personal sample on Ron Maker on October 23 1995 during excavating and cleaning rocks by compressed air were below OSHA PEL and ACGIH TLV limits
The SSHO performed noise monitoring according to the HSP at the exclusion zone and at the Barcelona Avenue site perimeter fence A Dupont sound level meter was used for noise monitoring The noise level in the exclusion zone during all operations except one did not exceed the on site criteria of 85 dB(a) During a short time when the air compressor had been used to clean rocks the sound level in the exclusion zone next to the air compressor did exceed 85 dB(a) Ear protection devices were worn by the workers during that operation At no time did the noise level at the Barcelona Avenue site perimeter exceed 10 dB(a) above the ambient noise level or 85 dB(a)
The SSHO performed total dust monitoring on a daily basis during the project at the site perimeter downwind of work location and at the site gate using a Miniram real time dust meter The summary of dust monitoring is presented in Table No 2 Total dust concentrations on site and off site did not exceed site criteria of 1 mgm3 and the action level of 05 nigny1
The summary of air monitoring for Volatile Organic Compounds (VOC) is presented in Table No 3 VOC concentrations in the working area did not exceed the on site criteria of 5 ppm in a breathing zone VOC concentrations on the site perimeter did not exceed real time off site criteria of 2 ppm
Five detail reports with results of air sampling were submitted during the project period
Sincerely Cashins amp Associates Inc
Evelina Vaughan Industrial Hygieflfst
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PROJECT NAME_ SITE LOCATION
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CASHINS amp Associates Inc
WBBKLY HEALTH amp SAFETY FLAK COMPLIANCE SUMMARY REPORT
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- barcode 14732
- barcodetext SEMS Doc ID 14732
![Page 40: SALEM ACRES SUPERFUND SITE SALEM, MA ...The truck loading pa d consisted of a crushed stone are sea t up along the east sid e o f SL-4 adjacent to the access road A. row of concrete](https://reader036.vdocuments.us/reader036/viewer/2022070114/60729b840fec4e6b4d136a16/html5/thumbnails/40.jpg)
HEALTH AND SAFETY PHASE-OUT REPORT SALEM ACRES SL-4 AREA
Introduction
During remediation work on SL-4 Health and Safety Monitoring was performed Cashins amp Associates Inc of Reading MA performed the following work as a subcontractor to TFCI
1) Preparation of a site-specific Health and Safety Plan (dated September 1 1995)
2) Provide a Field TechnicianIndustrial Hygienist to serve as Site Safety and Health Officer (SSHO) and to conduct air and noise monitoring
3) Provide a Certified Industrial Hygienist to review Health and Safety and to conduct site specific training (record of training included at end of Appendix C)
4) Collect 8-hour air samples for worker exposure and ambient air at the Barcelona Avenue gate Arrange for analysis of the samples and report results
5) Prepare daily and weekly Health and Safety reports
6) Prepare a Health and Safety Phase-Out Report
In general the following health and safety practices were followed
1) All workers wore hard hats safety glasses work boots gloves and hearing protection as minimum level PPE
2) When working in the exclusion zone workers wore in addition to above tyvek rubber overboots and rubber coated gloves When dust was a potential concern an industrial grade dustmist mask was also worn This level of PPE was considered Level D modified
3) Workers leaving the exclusion zone removed PPE (tyveks gloves boots and masks) in the support zone and either disposed of the items or decontaminated them
4) Workers andor visitors without 40-hour OSHA training were not permitted to enter the exclusion zone
Attached is a report prepared by Cashins amp Associates along with weekly Health and Safety Summary Reports prepared by the Field Hygienist In summary the air monitoring results indicate no levels exceeding the applicable exposure guidelines except one instance
During excavation of contaminated overburden in the northwest comer of the site an area of VOC contaminated soil was encountered Total VOCs levels measured using a PID exceeded the action level established in the Health and Safety Plan The SSHO advised TFCI to upgrade to Level C PPE in order to backfill the excavation in this area TFCI equipment operator upgraded and backfilled the area The SSHO in consultation with the Cashins CIH advised TFCI to avoid work in this area until the contaminants were characterized GEI sampled the material for waste characterization analysis and provided the results to TFCI Based on the results an action level was established by the CIH for the specific contaminants found Further PID measurements indicated levels below the new action level and work was resumed
The noise monitoring indicated that the noise level at the Barcelona Avenue gate was not exceeded Only one instance of excess noise level in the work zone was recorded (10 db(a) above the ambient noise level or 85 db(a)) Workers wore hearing protection in this instance
mdash 07171996 1601 6179444032 CASHIMS S ASSOCIATES PAGE 02
CASHINS amp Associates Inc
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July 17 1996
Mr Jack Enos T Ford Company Inc USTenney Street Georgetown MA 01833
Dear Jack
The Site Safety and Health Officer (SSHO) from Cashing amp Associates Inc performed daily inspections of the SL-4 area Salem Acres Superfund Site between 9595 and 12195 in accordance with the Health amp Safety Plan (HSP) for the site Daily inspection logs were submitted every day No accidentsincidents were reported during the work period
In accordance with the Health amp Safety Plan the SSHO performed daily air and noise monitoring at the site during Ac project Samples were collected for metals (lead beryllium chromium arsenic) and Polynuclear Aromatic Hydrocarbons (PAHs) at the site perimeter and for workers exposure determination Coal Tar Pitch Volatiles (a benzene soluble extractables) were also used to determine the workers exposure to PAH compounds Coal Tar Pitch Volatiles (CTPV) were analyzed using OSHA 58 Method If CTPV levels oq personal samples exceed the site criteria of 02 ragm3 the sample was submitted for PAHs analysis All air samples on the site perimeter were analyzed for PAH compounds
Site monitoring air sample collection and results report were done under the supervision of a Certified Industrial Hygienist
Full shift personal worker exposure samples were collected once a week Ambient air samples were collected at the Barcelona Avenue gate about 20 feet to the west of the site gate to determine if site contaminants were migrating off site The ambient air samples were also collected once a week during the project except on rainy days and days without work with contaminated soil
All air samples were analyzed by the American Industrial Hygiene Association accredited ESA Laboratories Inc using the following methods PAHs - NIOSH 5515 Lead - NIOSH 7082 Beryllium - NIOSH 7102 Chromium - NIOSH 7024 Arsenic - NIOSH 7900 Coal Tar Pitch Volatiles - OSHA 58 All methods used are accepted by the industrial hygiene community for 8-hour exposure assessment EPA methods are usually used for ambient air measurements
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07171996 1601 6179444032 CASHIMS amp ASSOCIATES PAGE 03
The results of air samples for metals and PAHs are presented in Table No 1
All concentrations of metals and PAHs at the site perimeter (Barcelona Avenue) and active work zones were below the OSHA Permissible Exposure Limits (PEL) and the American Conference of Governmental Industrial Hygicnists Threshold Limit Value (ACGIH TLV) Two personal samples collected on October 19 and October 23rd showed Coal Tar Pitch Volatiles (CTPV) results above OSHA PEL and AIHA TLV limits Both samples were resubmittcd to the lab for further analysis to determine if PAH compounds are present because the CTPV results were above site criteria
The results of the PAH concentrations for the personal sample on Mark Goodwin on October 19 1995 during excavation and washing trucks and for the personal sample on Ron Maker on October 23 1995 during excavating and cleaning rocks by compressed air were below OSHA PEL and ACGIH TLV limits
The SSHO performed noise monitoring according to the HSP at the exclusion zone and at the Barcelona Avenue site perimeter fence A Dupont sound level meter was used for noise monitoring The noise level in the exclusion zone during all operations except one did not exceed the on site criteria of 85 dB(a) During a short time when the air compressor had been used to clean rocks the sound level in the exclusion zone next to the air compressor did exceed 85 dB(a) Ear protection devices were worn by the workers during that operation At no time did the noise level at the Barcelona Avenue site perimeter exceed 10 dB(a) above the ambient noise level or 85 dB(a)
The SSHO performed total dust monitoring on a daily basis during the project at the site perimeter downwind of work location and at the site gate using a Miniram real time dust meter The summary of dust monitoring is presented in Table No 2 Total dust concentrations on site and off site did not exceed site criteria of 1 mgm3 and the action level of 05 nigny1
The summary of air monitoring for Volatile Organic Compounds (VOC) is presented in Table No 3 VOC concentrations in the working area did not exceed the on site criteria of 5 ppm in a breathing zone VOC concentrations on the site perimeter did not exceed real time off site criteria of 2 ppm
Five detail reports with results of air sampling were submitted during the project period
Sincerely Cashins amp Associates Inc
Evelina Vaughan Industrial Hygieflfst
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Industrial Hygiene amp Environmental Testing
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CASHINS amp Associates inc
Ifxtuitral Hygltne A fnvironmtnltt Tuning
W3SXLY HBALTH amp SAFETY PLAN COMPLIANCE SUMMARY R3PORT
CLIENT T foyd C o m a n
LOCATION gal era Acres Sx^perfund Site 8L-4 Area
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55 CAMBRIDGE STREET bull SUITE 201 bull BURLINGTON MA 01803 laquo TEL 61 -273-9080 bull FAX 67-273-9C84
09111995 1023 6172739084 CASHINS ASSOCIATES PAGE 01
CASHINSamp Associates Inc
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WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Fprd Company
LOCATION Salen Acres Suoerfund Site SL-4 Area
DATES INCLUDED IN SUMMARY
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CASHINS amp Associates Inc
Industrial Hygitnf amp CmimnmenUl Tinting
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Compan
LOCATION Salem Acres Superfund Site SL-4 Area
DATES INCLUDED IN SUMMARY
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CASHINSamp Associates Inc
Intutttitl Myffcnt t InvtmnmmUt Itnl
WEEKLY HEALTH 6 SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Fortjl Cqjapany
LOCATION Salem Acrlaquoa Superfund Site 9L-4 Area
DATES INCLUDED IN SUMMARY
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55 CAMBRIDGE STREFT SUITE 201 bull BURUNCTON MA oisoa bull TEL 617-273-9030 bull FAX 6i 7-273-9084
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OSHINSamp Associates Inc
Industrial Hygiene amp Emironmvntal Testing
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Company
LOCATION Salem Acres Superfund Site SL-4 Area
DATES INCLUDED IN SUMMARY J_
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CASHINS amp Associates Inc
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ISSUED TO REPRESENTING
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PROJECT NAME_ SITE LOCATION
THE PURPOSE OF THE FOLLOWING STATEMENT IS TO DOCUMENT THE EXISTENCE OF A CONDITION OR CONCERN WHICH CASHINS amp ASSOCIATES INC BELIEVES WARRANTS IMMEDIATE CORRECTIVE ACTION POSSIBLE SOLUTIONS AND OR CORRECTIVE ACTIONS WILL BE INCLUDED IN THIS NOTIFICATION WHEN POSSIBLE THIS NOTIFICATION IS LIMITED TO SITUATIONS THAT REPRESENT EITHER IMMEDIATE DANGER TO LIFE OR HEALTH CONDITIONS OR PREVIOUSLY IDENTIFIED CHRONIC PROBLEMS THAT UNDERMINE OUR ABILITY TO EFFECTIVELY INSURE COMPLIANCE WITH THE REQUIREMENTS OF THE HEALTH AND SAFETY PLAN
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CISHINS amp Associates Inc
Industrial Hygirne amp Cmimnmtntal Testing
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Company
LOCATION Salem Acres Superfund Site SL-4 Area
DATES INCLUDED IN SUMMARY T
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CLIENT T Ford Coqpanv
LOCATION Sa^am Acras Super fund 5 jte SL-4 Area
DATES INCLUDED IN SUMMARY bull
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07161996 1650 617944408 CASHING 3 ASSOCIATES PAGE 05
CASHINSamp Associates Inc
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CLIENT t T Ford Coimbanv
LOCATION t Salam Acraa Suoarfund Site SL-4 Arlaquoa
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CASHIMS amp ASSOCIATES PAGE 04 07161996 1658 6179444032
OVSHINSamp Associates Inc
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Company T
LOCATION Salem AcrM Suoerfund Stta 8L-4 Araa
DATES INCLUDED IN SUMMARY
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55 CAMBRIDGE STREET bull SUITE 201 bull BURUNGTON MA 01803 bull TEL 617-273-9080 bull FAX 617-273-9084
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07151996 18 fO 6179444082 CASHINS S ASSOCIATES PAGE 02
CASHINS amp Associates Inc
WBBKLY HEALTH amp SAFETY FLAK COMPLIANCE SUMMARY REPORT
CLIENT T Ford Compapv
LOCATION i Sal am Acrlaquolaquo Suparfund Sita SL-4 Area
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- barcode 14732
- barcodetext SEMS Doc ID 14732
![Page 41: SALEM ACRES SUPERFUND SITE SALEM, MA ...The truck loading pa d consisted of a crushed stone are sea t up along the east sid e o f SL-4 adjacent to the access road A. row of concrete](https://reader036.vdocuments.us/reader036/viewer/2022070114/60729b840fec4e6b4d136a16/html5/thumbnails/41.jpg)
During excavation of contaminated overburden in the northwest comer of the site an area of VOC contaminated soil was encountered Total VOCs levels measured using a PID exceeded the action level established in the Health and Safety Plan The SSHO advised TFCI to upgrade to Level C PPE in order to backfill the excavation in this area TFCI equipment operator upgraded and backfilled the area The SSHO in consultation with the Cashins CIH advised TFCI to avoid work in this area until the contaminants were characterized GEI sampled the material for waste characterization analysis and provided the results to TFCI Based on the results an action level was established by the CIH for the specific contaminants found Further PID measurements indicated levels below the new action level and work was resumed
The noise monitoring indicated that the noise level at the Barcelona Avenue gate was not exceeded Only one instance of excess noise level in the work zone was recorded (10 db(a) above the ambient noise level or 85 db(a)) Workers wore hearing protection in this instance
mdash 07171996 1601 6179444032 CASHIMS S ASSOCIATES PAGE 02
CASHINS amp Associates Inc
ItxhalrM Hy-gifnr A Invtronmtnltl Tttling
July 17 1996
Mr Jack Enos T Ford Company Inc USTenney Street Georgetown MA 01833
Dear Jack
The Site Safety and Health Officer (SSHO) from Cashing amp Associates Inc performed daily inspections of the SL-4 area Salem Acres Superfund Site between 9595 and 12195 in accordance with the Health amp Safety Plan (HSP) for the site Daily inspection logs were submitted every day No accidentsincidents were reported during the work period
In accordance with the Health amp Safety Plan the SSHO performed daily air and noise monitoring at the site during Ac project Samples were collected for metals (lead beryllium chromium arsenic) and Polynuclear Aromatic Hydrocarbons (PAHs) at the site perimeter and for workers exposure determination Coal Tar Pitch Volatiles (a benzene soluble extractables) were also used to determine the workers exposure to PAH compounds Coal Tar Pitch Volatiles (CTPV) were analyzed using OSHA 58 Method If CTPV levels oq personal samples exceed the site criteria of 02 ragm3 the sample was submitted for PAHs analysis All air samples on the site perimeter were analyzed for PAH compounds
Site monitoring air sample collection and results report were done under the supervision of a Certified Industrial Hygienist
Full shift personal worker exposure samples were collected once a week Ambient air samples were collected at the Barcelona Avenue gate about 20 feet to the west of the site gate to determine if site contaminants were migrating off site The ambient air samples were also collected once a week during the project except on rainy days and days without work with contaminated soil
All air samples were analyzed by the American Industrial Hygiene Association accredited ESA Laboratories Inc using the following methods PAHs - NIOSH 5515 Lead - NIOSH 7082 Beryllium - NIOSH 7102 Chromium - NIOSH 7024 Arsenic - NIOSH 7900 Coal Tar Pitch Volatiles - OSHA 58 All methods used are accepted by the industrial hygiene community for 8-hour exposure assessment EPA methods are usually used for ambient air measurements
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80 Mam Street bull Reading MA 01867 bull Phone- 61 7-944-4060 bull Fax 61 7-944-4082
07171996 1601 6179444032 CASHIMS amp ASSOCIATES PAGE 03
The results of air samples for metals and PAHs are presented in Table No 1
All concentrations of metals and PAHs at the site perimeter (Barcelona Avenue) and active work zones were below the OSHA Permissible Exposure Limits (PEL) and the American Conference of Governmental Industrial Hygicnists Threshold Limit Value (ACGIH TLV) Two personal samples collected on October 19 and October 23rd showed Coal Tar Pitch Volatiles (CTPV) results above OSHA PEL and AIHA TLV limits Both samples were resubmittcd to the lab for further analysis to determine if PAH compounds are present because the CTPV results were above site criteria
The results of the PAH concentrations for the personal sample on Mark Goodwin on October 19 1995 during excavation and washing trucks and for the personal sample on Ron Maker on October 23 1995 during excavating and cleaning rocks by compressed air were below OSHA PEL and ACGIH TLV limits
The SSHO performed noise monitoring according to the HSP at the exclusion zone and at the Barcelona Avenue site perimeter fence A Dupont sound level meter was used for noise monitoring The noise level in the exclusion zone during all operations except one did not exceed the on site criteria of 85 dB(a) During a short time when the air compressor had been used to clean rocks the sound level in the exclusion zone next to the air compressor did exceed 85 dB(a) Ear protection devices were worn by the workers during that operation At no time did the noise level at the Barcelona Avenue site perimeter exceed 10 dB(a) above the ambient noise level or 85 dB(a)
The SSHO performed total dust monitoring on a daily basis during the project at the site perimeter downwind of work location and at the site gate using a Miniram real time dust meter The summary of dust monitoring is presented in Table No 2 Total dust concentrations on site and off site did not exceed site criteria of 1 mgm3 and the action level of 05 nigny1
The summary of air monitoring for Volatile Organic Compounds (VOC) is presented in Table No 3 VOC concentrations in the working area did not exceed the on site criteria of 5 ppm in a breathing zone VOC concentrations on the site perimeter did not exceed real time off site criteria of 2 ppm
Five detail reports with results of air sampling were submitted during the project period
Sincerely Cashins amp Associates Inc
Evelina Vaughan Industrial Hygieflfst
CASHINS amp ASSOCIATES Inc
80 Mam Street bull Reading MA 01867 bull Phone61 7-944-4060 bull Fax 617-944-4082
07171996 1601 6179444082 CASHINS S ASSOCIATES PAGE 04
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CASHINS amp Associates inc
Ifxtuitral Hygltne A fnvironmtnltt Tuning
W3SXLY HBALTH amp SAFETY PLAN COMPLIANCE SUMMARY R3PORT
CLIENT T foyd C o m a n
LOCATION gal era Acres Sx^perfund Site 8L-4 Area
DATES INCLUDED IN SUMMARY
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55 CAMBRIDGE STREET bull SUITE 201 bull BURLINGTON MA 01803 laquo TEL 61 -273-9080 bull FAX 67-273-9C84
09111995 1023 6172739084 CASHINS ASSOCIATES PAGE 01
CASHINSamp Associates Inc
Induttrml Hygttnr t Emtroomtnttl Ttstinf
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Fprd Company
LOCATION Salen Acres Suoerfund Site SL-4 Area
DATES INCLUDED IN SUMMARY
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55 CAMBRIDGE STREET bull SUITE 201 bull BURLINGTON MA 01803 raquo- TEL 6J 7-273-9080 bull FAX 617-273-9084
CASHINS amp Associates Inc
Industrial Hygitnf amp CmimnmenUl Tinting
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Compan
LOCATION Salem Acres Superfund Site SL-4 Area
DATES INCLUDED IN SUMMARY
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CASHING X ASSOCIATES PAGE
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WEEKLY HEALTH amp SAFBTT PLAN COMPLIANCE SUMMARY REPORT
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LOCATION Salam Aerag SL-4
DATES INCLUDED IN SUMMARY
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CASHINSamp Associates Inc
Intutttitl Myffcnt t InvtmnmmUt Itnl
WEEKLY HEALTH 6 SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Fortjl Cqjapany
LOCATION Salem Acrlaquoa Superfund Site 9L-4 Area
DATES INCLUDED IN SUMMARY
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SUMMARIZED BY FOR CASKINS amp ASSOCIATES INC
55 CAMBRIDGE STREFT SUITE 201 bull BURUNCTON MA oisoa bull TEL 617-273-9030 bull FAX 6i 7-273-9084
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OSHINSamp Associates Inc
Industrial Hygiene amp Emironmvntal Testing
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Company
LOCATION Salem Acres Superfund Site SL-4 Area
DATES INCLUDED IN SUMMARY J_
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5 CAMBRIDGE STREET bull SUITE JO I bull BURLINGTON MA 01 K03 TEL ltjl 7-J7J-9080 bull FAX b I 7-273-9084
CASHINS amp Associates Inc
Industrial Hygifnr amp [nvironmenljl res
SERIOUS HAZARD NOTIFICATION
ISSUED TO REPRESENTING
ISSUED BY REPRESENTING CASHINS S ASSOCIATES INcT DAY DATE ISSUED O04Xmdash 1 bull-bullmdashbull f P^JT
PROJECT NAME_ SITE LOCATION
THE PURPOSE OF THE FOLLOWING STATEMENT IS TO DOCUMENT THE EXISTENCE OF A CONDITION OR CONCERN WHICH CASHINS amp ASSOCIATES INC BELIEVES WARRANTS IMMEDIATE CORRECTIVE ACTION POSSIBLE SOLUTIONS AND OR CORRECTIVE ACTIONS WILL BE INCLUDED IN THIS NOTIFICATION WHEN POSSIBLE THIS NOTIFICATION IS LIMITED TO SITUATIONS THAT REPRESENT EITHER IMMEDIATE DANGER TO LIFE OR HEALTH CONDITIONS OR PREVIOUSLY IDENTIFIED CHRONIC PROBLEMS THAT UNDERMINE OUR ABILITY TO EFFECTIVELY INSURE COMPLIANCE WITH THE REQUIREMENTS OF THE HEALTH AND SAFETY PLAN
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55 CAMBRIDGE STREET bull SUITE 201 bull BURLINGTON MA 01 803 bull TEL 61 7-273-9080 bull FAX fgtl 7-273-9084
CISHINS amp Associates Inc
Industrial Hygirne amp Cmimnmtntal Testing
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Company
LOCATION Salem Acres Superfund Site SL-4 Area
DATES INCLUDED IN SUMMARY T
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CASHINSamp Associates Inc
WEEKLY HEALTH amp SA7STT PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Coqpanv
LOCATION Sa^am Acras Super fund 5 jte SL-4 Area
DATES INCLUDED IN SUMMARY bull
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CASHINSamp Associates Inc
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LOCATION Salem Acraa Suoerfund Sita 5L-4
DATES INCLUDED IN SUMMARY bull
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55 CAMBRIDGE STREET bullSUITE 201 bull BURllNCTON MA 01803 bull TEL 617-273-9080 bull FAX 617-273-9084
07161996 1650 617944408 CASHING 3 ASSOCIATES PAGE 05
CASHINSamp Associates Inc
fmimnntattl few
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CLIENT t T Ford Coimbanv
LOCATION t Salam Acraa Suoarfund Site SL-4 Arlaquoa
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55 CAMBRIDGE STREET bull SUITE 201 bull BURLINGTON MA 01803 lt TEL 617-273-9080 bull FAX 617-273-9084
CASHIMS amp ASSOCIATES PAGE 04 07161996 1658 6179444032
OVSHINSamp Associates Inc
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Company T
LOCATION Salem AcrM Suoerfund Stta 8L-4 Araa
DATES INCLUDED IN SUMMARY
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55 CAMBRIDGE STREET bull SUITE 201 bull BURUNGTON MA 01803 bull TEL 617-273-9080 bull FAX 617-273-9084
07161996 1658 6179444082 CASHIMS 3 ASSOCIATES PAGE 03
CASHINSamp Associates Inc
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LOCATION Sal era Acraa Suplaquorfund Sj-ta 8L-4 Araa
DATES INCLUDED IN SUMMARY
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55 CAMBRIDGE STREET bull SUITE 201 bull 8URUNGTON MA 01803 bull TEL 617-273-9080 bull FAX 617-273-90W
07151996 18 fO 6179444082 CASHINS S ASSOCIATES PAGE 02
CASHINS amp Associates Inc
WBBKLY HEALTH amp SAFETY FLAK COMPLIANCE SUMMARY REPORT
CLIENT T Ford Compapv
LOCATION i Sal am Acrlaquolaquo Suparfund Sita SL-4 Area
DATES INCLUDED IN SUMMARY i bull pound7 mdash
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- barcode 14732
- barcodetext SEMS Doc ID 14732
![Page 42: SALEM ACRES SUPERFUND SITE SALEM, MA ...The truck loading pa d consisted of a crushed stone are sea t up along the east sid e o f SL-4 adjacent to the access road A. row of concrete](https://reader036.vdocuments.us/reader036/viewer/2022070114/60729b840fec4e6b4d136a16/html5/thumbnails/42.jpg)
mdash 07171996 1601 6179444032 CASHIMS S ASSOCIATES PAGE 02
CASHINS amp Associates Inc
ItxhalrM Hy-gifnr A Invtronmtnltl Tttling
July 17 1996
Mr Jack Enos T Ford Company Inc USTenney Street Georgetown MA 01833
Dear Jack
The Site Safety and Health Officer (SSHO) from Cashing amp Associates Inc performed daily inspections of the SL-4 area Salem Acres Superfund Site between 9595 and 12195 in accordance with the Health amp Safety Plan (HSP) for the site Daily inspection logs were submitted every day No accidentsincidents were reported during the work period
In accordance with the Health amp Safety Plan the SSHO performed daily air and noise monitoring at the site during Ac project Samples were collected for metals (lead beryllium chromium arsenic) and Polynuclear Aromatic Hydrocarbons (PAHs) at the site perimeter and for workers exposure determination Coal Tar Pitch Volatiles (a benzene soluble extractables) were also used to determine the workers exposure to PAH compounds Coal Tar Pitch Volatiles (CTPV) were analyzed using OSHA 58 Method If CTPV levels oq personal samples exceed the site criteria of 02 ragm3 the sample was submitted for PAHs analysis All air samples on the site perimeter were analyzed for PAH compounds
Site monitoring air sample collection and results report were done under the supervision of a Certified Industrial Hygienist
Full shift personal worker exposure samples were collected once a week Ambient air samples were collected at the Barcelona Avenue gate about 20 feet to the west of the site gate to determine if site contaminants were migrating off site The ambient air samples were also collected once a week during the project except on rainy days and days without work with contaminated soil
All air samples were analyzed by the American Industrial Hygiene Association accredited ESA Laboratories Inc using the following methods PAHs - NIOSH 5515 Lead - NIOSH 7082 Beryllium - NIOSH 7102 Chromium - NIOSH 7024 Arsenic - NIOSH 7900 Coal Tar Pitch Volatiles - OSHA 58 All methods used are accepted by the industrial hygiene community for 8-hour exposure assessment EPA methods are usually used for ambient air measurements
CRErORTTFOmiOO
80 Mam Street bull Reading MA 01867 bull Phone- 61 7-944-4060 bull Fax 61 7-944-4082
07171996 1601 6179444032 CASHIMS amp ASSOCIATES PAGE 03
The results of air samples for metals and PAHs are presented in Table No 1
All concentrations of metals and PAHs at the site perimeter (Barcelona Avenue) and active work zones were below the OSHA Permissible Exposure Limits (PEL) and the American Conference of Governmental Industrial Hygicnists Threshold Limit Value (ACGIH TLV) Two personal samples collected on October 19 and October 23rd showed Coal Tar Pitch Volatiles (CTPV) results above OSHA PEL and AIHA TLV limits Both samples were resubmittcd to the lab for further analysis to determine if PAH compounds are present because the CTPV results were above site criteria
The results of the PAH concentrations for the personal sample on Mark Goodwin on October 19 1995 during excavation and washing trucks and for the personal sample on Ron Maker on October 23 1995 during excavating and cleaning rocks by compressed air were below OSHA PEL and ACGIH TLV limits
The SSHO performed noise monitoring according to the HSP at the exclusion zone and at the Barcelona Avenue site perimeter fence A Dupont sound level meter was used for noise monitoring The noise level in the exclusion zone during all operations except one did not exceed the on site criteria of 85 dB(a) During a short time when the air compressor had been used to clean rocks the sound level in the exclusion zone next to the air compressor did exceed 85 dB(a) Ear protection devices were worn by the workers during that operation At no time did the noise level at the Barcelona Avenue site perimeter exceed 10 dB(a) above the ambient noise level or 85 dB(a)
The SSHO performed total dust monitoring on a daily basis during the project at the site perimeter downwind of work location and at the site gate using a Miniram real time dust meter The summary of dust monitoring is presented in Table No 2 Total dust concentrations on site and off site did not exceed site criteria of 1 mgm3 and the action level of 05 nigny1
The summary of air monitoring for Volatile Organic Compounds (VOC) is presented in Table No 3 VOC concentrations in the working area did not exceed the on site criteria of 5 ppm in a breathing zone VOC concentrations on the site perimeter did not exceed real time off site criteria of 2 ppm
Five detail reports with results of air sampling were submitted during the project period
Sincerely Cashins amp Associates Inc
Evelina Vaughan Industrial Hygieflfst
CASHINS amp ASSOCIATES Inc
80 Mam Street bull Reading MA 01867 bull Phone61 7-944-4060 bull Fax 617-944-4082
07171996 1601 6179444082 CASHINS S ASSOCIATES PAGE 04
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89111995 1023 6172733(384 CASHINS ASSOCIATES PAGE 01
CASHINS amp Associates inc
Ifxtuitral Hygltne A fnvironmtnltt Tuning
W3SXLY HBALTH amp SAFETY PLAN COMPLIANCE SUMMARY R3PORT
CLIENT T foyd C o m a n
LOCATION gal era Acres Sx^perfund Site 8L-4 Area
DATES INCLUDED IN SUMMARY
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SUMMARIZED BY FOR CASHINS amp ASSOCIATES INC
55 CAMBRIDGE STREET bull SUITE 201 bull BURLINGTON MA 01803 laquo TEL 61 -273-9080 bull FAX 67-273-9C84
09111995 1023 6172739084 CASHINS ASSOCIATES PAGE 01
CASHINSamp Associates Inc
Induttrml Hygttnr t Emtroomtnttl Ttstinf
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Fprd Company
LOCATION Salen Acres Suoerfund Site SL-4 Area
DATES INCLUDED IN SUMMARY
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SUMMARIZED BY FOR CASHINS 4 ASSOCIATES INC
55 CAMBRIDGE STREET bull SUITE 201 bull BURLINGTON MA 01803 raquo- TEL 6J 7-273-9080 bull FAX 617-273-9084
CASHINS amp Associates Inc
Industrial Hygitnf amp CmimnmenUl Tinting
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Compan
LOCATION Salem Acres Superfund Site SL-4 Area
DATES INCLUDED IN SUMMARY
-amp
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CASHING X ASSOCIATES PAGE
1C n -044408shy07161336 1650 61 344408shy
CASHINSamp Associates Inc
WEEKLY HEALTH amp SAFBTT PLAN COMPLIANCE SUMMARY REPORT
CLIENT ^T Ford Combanv
LOCATION Salam Aerag SL-4
DATES INCLUDED IN SUMMARY
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SUMMARIZED BY FOR CASHINS amp ASSOCIATES INC
55 CAMBRIDGE STREET bull SUITE 201 bull SURUNCTON vu 01803 TEL 61 rori-^oao FAX 61 ~ rj
07161996 1650 6179444082 CASHI MS amp ASSOCIATES PAGE 10
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55 CAM8RJDCpound STWET bull SUTTE201 eolaquolNCTONMAOJlaquo03 TIL 6t7shy
07161996 1650 6179444082 CASH INS amp ASSOCIATES PAGE 08
CASHINSamp Associates Inc
Intutttitl Myffcnt t InvtmnmmUt Itnl
WEEKLY HEALTH 6 SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Fortjl Cqjapany
LOCATION Salem Acrlaquoa Superfund Site 9L-4 Area
DATES INCLUDED IN SUMMARY
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CLIENT T Ford Company
LOCATION Salem Acres Superfund Site SL-4 Area
DATES INCLUDED IN SUMMARY J_
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CISHINS amp Associates Inc
Industrial Hygirne amp Cmimnmtntal Testing
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Company
LOCATION Salem Acres Superfund Site SL-4 Area
DATES INCLUDED IN SUMMARY T
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LOCATION Sa^am Acras Super fund 5 jte SL-4 Area
DATES INCLUDED IN SUMMARY bull
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55 CAMBRIDGE STREET bullSUITE 201 bull BURllNCTON MA 01803 bull TEL 617-273-9080 bull FAX 617-273-9084
07161996 1650 617944408 CASHING 3 ASSOCIATES PAGE 05
CASHINSamp Associates Inc
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LOCATION t Salam Acraa Suoarfund Site SL-4 Arlaquoa
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CASHIMS amp ASSOCIATES PAGE 04 07161996 1658 6179444032
OVSHINSamp Associates Inc
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Company T
LOCATION Salem AcrM Suoerfund Stta 8L-4 Araa
DATES INCLUDED IN SUMMARY
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55 CAMBRIDGE STREET bull SUITE 201 bull BURUNGTON MA 01803 bull TEL 617-273-9080 bull FAX 617-273-9084
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07151996 18 fO 6179444082 CASHINS S ASSOCIATES PAGE 02
CASHINS amp Associates Inc
WBBKLY HEALTH amp SAFETY FLAK COMPLIANCE SUMMARY REPORT
CLIENT T Ford Compapv
LOCATION i Sal am Acrlaquolaquo Suparfund Sita SL-4 Area
DATES INCLUDED IN SUMMARY i bull pound7 mdash
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- barcode 14732
- barcodetext SEMS Doc ID 14732
![Page 43: SALEM ACRES SUPERFUND SITE SALEM, MA ...The truck loading pa d consisted of a crushed stone are sea t up along the east sid e o f SL-4 adjacent to the access road A. row of concrete](https://reader036.vdocuments.us/reader036/viewer/2022070114/60729b840fec4e6b4d136a16/html5/thumbnails/43.jpg)
07171996 1601 6179444032 CASHIMS amp ASSOCIATES PAGE 03
The results of air samples for metals and PAHs are presented in Table No 1
All concentrations of metals and PAHs at the site perimeter (Barcelona Avenue) and active work zones were below the OSHA Permissible Exposure Limits (PEL) and the American Conference of Governmental Industrial Hygicnists Threshold Limit Value (ACGIH TLV) Two personal samples collected on October 19 and October 23rd showed Coal Tar Pitch Volatiles (CTPV) results above OSHA PEL and AIHA TLV limits Both samples were resubmittcd to the lab for further analysis to determine if PAH compounds are present because the CTPV results were above site criteria
The results of the PAH concentrations for the personal sample on Mark Goodwin on October 19 1995 during excavation and washing trucks and for the personal sample on Ron Maker on October 23 1995 during excavating and cleaning rocks by compressed air were below OSHA PEL and ACGIH TLV limits
The SSHO performed noise monitoring according to the HSP at the exclusion zone and at the Barcelona Avenue site perimeter fence A Dupont sound level meter was used for noise monitoring The noise level in the exclusion zone during all operations except one did not exceed the on site criteria of 85 dB(a) During a short time when the air compressor had been used to clean rocks the sound level in the exclusion zone next to the air compressor did exceed 85 dB(a) Ear protection devices were worn by the workers during that operation At no time did the noise level at the Barcelona Avenue site perimeter exceed 10 dB(a) above the ambient noise level or 85 dB(a)
The SSHO performed total dust monitoring on a daily basis during the project at the site perimeter downwind of work location and at the site gate using a Miniram real time dust meter The summary of dust monitoring is presented in Table No 2 Total dust concentrations on site and off site did not exceed site criteria of 1 mgm3 and the action level of 05 nigny1
The summary of air monitoring for Volatile Organic Compounds (VOC) is presented in Table No 3 VOC concentrations in the working area did not exceed the on site criteria of 5 ppm in a breathing zone VOC concentrations on the site perimeter did not exceed real time off site criteria of 2 ppm
Five detail reports with results of air sampling were submitted during the project period
Sincerely Cashins amp Associates Inc
Evelina Vaughan Industrial Hygieflfst
CASHINS amp ASSOCIATES Inc
80 Mam Street bull Reading MA 01867 bull Phone61 7-944-4060 bull Fax 617-944-4082
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CASHINS amp Associates inc
Ifxtuitral Hygltne A fnvironmtnltt Tuning
W3SXLY HBALTH amp SAFETY PLAN COMPLIANCE SUMMARY R3PORT
CLIENT T foyd C o m a n
LOCATION gal era Acres Sx^perfund Site 8L-4 Area
DATES INCLUDED IN SUMMARY
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55 CAMBRIDGE STREET bull SUITE 201 bull BURLINGTON MA 01803 laquo TEL 61 -273-9080 bull FAX 67-273-9C84
09111995 1023 6172739084 CASHINS ASSOCIATES PAGE 01
CASHINSamp Associates Inc
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CLIENT T Fprd Company
LOCATION Salen Acres Suoerfund Site SL-4 Area
DATES INCLUDED IN SUMMARY
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55 CAMBRIDGE STREET bull SUITE 201 bull BURLINGTON MA 01803 raquo- TEL 6J 7-273-9080 bull FAX 617-273-9084
CASHINS amp Associates Inc
Industrial Hygitnf amp CmimnmenUl Tinting
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Compan
LOCATION Salem Acres Superfund Site SL-4 Area
DATES INCLUDED IN SUMMARY
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CASHINSamp Associates Inc
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CLIENT T Fortjl Cqjapany
LOCATION Salem Acrlaquoa Superfund Site 9L-4 Area
DATES INCLUDED IN SUMMARY
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55 CAMBRIDGE STREFT SUITE 201 bull BURUNCTON MA oisoa bull TEL 617-273-9030 bull FAX 6i 7-273-9084
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Industrial Hygiene amp Emironmvntal Testing
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Company
LOCATION Salem Acres Superfund Site SL-4 Area
DATES INCLUDED IN SUMMARY J_
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Industrial Hygirne amp Cmimnmtntal Testing
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CLIENT T Ford Company
LOCATION Salem Acres Superfund Site SL-4 Area
DATES INCLUDED IN SUMMARY T
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CLIENT T Ford Coqpanv
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DATES INCLUDED IN SUMMARY bull
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07161996 1658 6179444032 CASHINS S ASSOCIATES PAGE 86
CASHINSamp Associates Inc
MtanW HriHtif A
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LOCATION Salem Acraa Suoerfund Sita 5L-4
DATES INCLUDED IN SUMMARY bull
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55 CAMBRIDGE STREET bullSUITE 201 bull BURllNCTON MA 01803 bull TEL 617-273-9080 bull FAX 617-273-9084
07161996 1650 617944408 CASHING 3 ASSOCIATES PAGE 05
CASHINSamp Associates Inc
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55 CAMBRIDGE STREET bull SUITE 201 bull BURLINGTON MA 01803 lt TEL 617-273-9080 bull FAX 617-273-9084
CASHIMS amp ASSOCIATES PAGE 04 07161996 1658 6179444032
OVSHINSamp Associates Inc
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Company T
LOCATION Salem AcrM Suoerfund Stta 8L-4 Araa
DATES INCLUDED IN SUMMARY
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- barcodetext SEMS Doc ID 14732
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LOCATION Salem Acres Superfund Site SL-4 Area
DATES INCLUDED IN SUMMARY
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55 CAMBRIDGE STREET bull SUITE 201 bull BURLINGTON MA 01803 laquo TEL 61 -273-9080 bull FAX 67-273-9C84
09111995 1023 6172739084 CASHINS ASSOCIATES PAGE 01
CASHINSamp Associates Inc
Induttrml Hygttnr t Emtroomtnttl Ttstinf
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Fprd Company
LOCATION Salen Acres Suoerfund Site SL-4 Area
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55 CAMBRIDGE STREET bull SUITE 201 bull BURLINGTON MA 01803 raquo- TEL 6J 7-273-9080 bull FAX 617-273-9084
CASHINS amp Associates Inc
Industrial Hygitnf amp CmimnmenUl Tinting
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Compan
LOCATION Salem Acres Superfund Site SL-4 Area
DATES INCLUDED IN SUMMARY
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55 CAMBRIDGE STREET bull SUITE 201 bull SURUNCTON vu 01803 TEL 61 rori-^oao FAX 61 ~ rj
07161996 1650 6179444082 CASHI MS amp ASSOCIATES PAGE 10
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LOCATION Salem Acres Superfund Site SL-4 Area
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DATES INCLUDED IN SUMMARY J_
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Ifxtuitral Hygltne A fnvironmtnltt Tuning
W3SXLY HBALTH amp SAFETY PLAN COMPLIANCE SUMMARY R3PORT
CLIENT T foyd C o m a n
LOCATION gal era Acres Sx^perfund Site 8L-4 Area
DATES INCLUDED IN SUMMARY
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SUMMARIZED BY FOR CASHINS amp ASSOCIATES INC
55 CAMBRIDGE STREET bull SUITE 201 bull BURLINGTON MA 01803 laquo TEL 61 -273-9080 bull FAX 67-273-9C84
09111995 1023 6172739084 CASHINS ASSOCIATES PAGE 01
CASHINSamp Associates Inc
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LOCATION Salen Acres Suoerfund Site SL-4 Area
DATES INCLUDED IN SUMMARY
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CASHINS amp Associates Inc
Industrial Hygitnf amp CmimnmenUl Tinting
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Compan
LOCATION Salem Acres Superfund Site SL-4 Area
DATES INCLUDED IN SUMMARY
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CASHINSamp Associates Inc
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WEEKLY HEALTH 6 SAFETY PLAN COMPLIANCE SUMMARY REPORT
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LOCATION Salem Acrlaquoa Superfund Site 9L-4 Area
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CLIENT T Ford Company
LOCATION Salem Acres Superfund Site SL-4 Area
DATES INCLUDED IN SUMMARY J_
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07161996 1658 6179444032 CASHINS S ASSOCIATES PAGE 86
CASHINSamp Associates Inc
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55 CAMBRIDGE STREET bullSUITE 201 bull BURllNCTON MA 01803 bull TEL 617-273-9080 bull FAX 617-273-9084
07161996 1650 617944408 CASHING 3 ASSOCIATES PAGE 05
CASHINSamp Associates Inc
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CASHIMS amp ASSOCIATES PAGE 04 07161996 1658 6179444032
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WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
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LOCATION Salem AcrM Suoerfund Stta 8L-4 Araa
DATES INCLUDED IN SUMMARY
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55 CAMBRIDGE STREET bull SUITE 201 bull BURUNGTON MA 01803 bull TEL 617-273-9080 bull FAX 617-273-9084
07161996 1658 6179444082 CASHIMS 3 ASSOCIATES PAGE 03
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07151996 18 fO 6179444082 CASHINS S ASSOCIATES PAGE 02
CASHINS amp Associates Inc
WBBKLY HEALTH amp SAFETY FLAK COMPLIANCE SUMMARY REPORT
CLIENT T Ford Compapv
LOCATION i Sal am Acrlaquolaquo Suparfund Sita SL-4 Area
DATES INCLUDED IN SUMMARY i bull pound7 mdash
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55 CAMBRIDGE STREET SUITE 201 bull SURtlNCTON MA 01803 TEL 617-273-9080 bull FAX 61 7-273-9084
- barcode 14732
- barcodetext SEMS Doc ID 14732
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DATE
LOCATION OF TRAINING $ALt_M ACu
TIME 9 ^ rW
NAME COMPANY SIGNATURE
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TIME
NAME COMPANY SIGNATURE
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DATE
LOCATION OF TRAINING
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Ifxtuitral Hygltne A fnvironmtnltt Tuning
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CLIENT T foyd C o m a n
LOCATION gal era Acres Sx^perfund Site 8L-4 Area
DATES INCLUDED IN SUMMARY
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SUMMARIZED BY FOR CASHINS amp ASSOCIATES INC
55 CAMBRIDGE STREET bull SUITE 201 bull BURLINGTON MA 01803 laquo TEL 61 -273-9080 bull FAX 67-273-9C84
09111995 1023 6172739084 CASHINS ASSOCIATES PAGE 01
CASHINSamp Associates Inc
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LOCATION Salen Acres Suoerfund Site SL-4 Area
DATES INCLUDED IN SUMMARY
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CASHINS amp Associates Inc
Industrial Hygitnf amp CmimnmenUl Tinting
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Compan
LOCATION Salem Acres Superfund Site SL-4 Area
DATES INCLUDED IN SUMMARY
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DATES INCLUDED IN SUMMARY
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LOCATION Salem Acres Superfund Site SL-4 Area
DATES INCLUDED IN SUMMARY J_
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Industrial Hygirne amp Cmimnmtntal Testing
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
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LOCATION Salem Acres Superfund Site SL-4 Area
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WEEKLY HEALTH amp SA7STT PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Coqpanv
LOCATION Sa^am Acras Super fund 5 jte SL-4 Area
DATES INCLUDED IN SUMMARY bull
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FOR CASHINS amp ASSOCIATES INC
53 CAMBRIDGE STREET bull SUTE40I bull BURIJSCTON MA 0803 TfL 61 7-273-908O bull FAX fairo-Jshy
07161996 1658 6179444032 CASHINS S ASSOCIATES PAGE 86
CASHINSamp Associates Inc
MtanW HriHtif A
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT ^ mdash
CLIENT T Ford Company
LOCATION Salem Acraa Suoerfund Sita 5L-4
DATES INCLUDED IN SUMMARY bull
6 03 HL fro- TH4-shy
lt Go
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fo
SUMMARIZED BY FOR CASHINS amp ASSOCIATES INC
55 CAMBRIDGE STREET bullSUITE 201 bull BURllNCTON MA 01803 bull TEL 617-273-9080 bull FAX 617-273-9084
07161996 1650 617944408 CASHING 3 ASSOCIATES PAGE 05
CASHINSamp Associates Inc
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CLIENT t T Ford Coimbanv
LOCATION t Salam Acraa Suoarfund Site SL-4 Arlaquoa
DATES INCLUDED IN SUMMARYj pound mdashiffofrshy f
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55 CAMBRIDGE STREET bull SUITE 201 bull BURLINGTON MA 01803 lt TEL 617-273-9080 bull FAX 617-273-9084
CASHIMS amp ASSOCIATES PAGE 04 07161996 1658 6179444032
OVSHINSamp Associates Inc
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Company T
LOCATION Salem AcrM Suoerfund Stta 8L-4 Araa
DATES INCLUDED IN SUMMARY
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SUMMARIZED BY pound FOR CASHINS amp ASSOCIATES INC
55 CAMBRIDGE STREET bull SUITE 201 bull BURUNGTON MA 01803 bull TEL 617-273-9080 bull FAX 617-273-9084
07161996 1658 6179444082 CASHIMS 3 ASSOCIATES PAGE 03
CASHINSamp Associates Inc
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DATES INCLUDED IN SUMMARY
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07151996 18 fO 6179444082 CASHINS S ASSOCIATES PAGE 02
CASHINS amp Associates Inc
WBBKLY HEALTH amp SAFETY FLAK COMPLIANCE SUMMARY REPORT
CLIENT T Ford Compapv
LOCATION i Sal am Acrlaquolaquo Suparfund Sita SL-4 Area
DATES INCLUDED IN SUMMARY i bull pound7 mdash
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SXWMARIZ2D BY FOR CASHINS amp ASSOCIATES INC (
55 CAMBRIDGE STREET SUITE 201 bull SURtlNCTON MA 01803 TEL 617-273-9080 bull FAX 61 7-273-9084
- barcode 14732
- barcodetext SEMS Doc ID 14732
![Page 51: SALEM ACRES SUPERFUND SITE SALEM, MA ...The truck loading pa d consisted of a crushed stone are sea t up along the east sid e o f SL-4 adjacent to the access road A. row of concrete](https://reader036.vdocuments.us/reader036/viewer/2022070114/60729b840fec4e6b4d136a16/html5/thumbnails/51.jpg)
CASHINS amp Associates Inc
Industrial Hygiene amp Environmental Testing
SITE SPECIFIC amp HAZARD COMMUNICATIONS TRAINING SIGN-IN SHEET
ftt poundpoundpound
DATE
LOCATION OF TRAINING $ALt_M ACu
TIME 9 ^ rW
NAME COMPANY SIGNATURE
40 SALEM ST bull LYNNFIELD MA 011J40 bull TEL 617-2-)5-J77J - FAX ()l7-MS-tUrj
OSHINSamp Associates Inc
Industrill Hygiene amp Environnivnljl fating
SITE SPECIFIC amp HAZARD COMMUNICATIONS TRAINING SIGN-IN SHEET
DATE poundLOCATION OF TRAINING
TIME
NAME COMPANY SIGNATURE
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40 SAUM ST bull LYNNFIELD MA (J1J40 bull TEL 617-2-T 1773 FAX (gtI7 M5-iU7i
CASHINS amp Associates Inc
Industrie Hygitmt amp tnvironmvnlal
SITE SPECIFIC amp HAZARD COMMUNICATIONS TRAINING SIGN-IN SHEET
DATE
LOCATION OF TRAINING
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NAME COMPANY SIGNATURE
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40 SALEM ST bull LYNNFIELD MA 01J40 bull TEL 617-245-J77J bull FAX (gtl7--IS4()rj
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CASHINS amp Associates inc
Ifxtuitral Hygltne A fnvironmtnltt Tuning
W3SXLY HBALTH amp SAFETY PLAN COMPLIANCE SUMMARY R3PORT
CLIENT T foyd C o m a n
LOCATION gal era Acres Sx^perfund Site 8L-4 Area
DATES INCLUDED IN SUMMARY
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SUMMARIZED BY FOR CASHINS amp ASSOCIATES INC
55 CAMBRIDGE STREET bull SUITE 201 bull BURLINGTON MA 01803 laquo TEL 61 -273-9080 bull FAX 67-273-9C84
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CASHINSamp Associates Inc
Induttrml Hygttnr t Emtroomtnttl Ttstinf
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Fprd Company
LOCATION Salen Acres Suoerfund Site SL-4 Area
DATES INCLUDED IN SUMMARY
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55 CAMBRIDGE STREET bull SUITE 201 bull BURLINGTON MA 01803 raquo- TEL 6J 7-273-9080 bull FAX 617-273-9084
CASHINS amp Associates Inc
Industrial Hygitnf amp CmimnmenUl Tinting
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Compan
LOCATION Salem Acres Superfund Site SL-4 Area
DATES INCLUDED IN SUMMARY
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CASHING X ASSOCIATES PAGE
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DATES INCLUDED IN SUMMARY
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07161996 1650 6179444082 CASH INS amp ASSOCIATES PAGE 08
CASHINSamp Associates Inc
Intutttitl Myffcnt t InvtmnmmUt Itnl
WEEKLY HEALTH 6 SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Fortjl Cqjapany
LOCATION Salem Acrlaquoa Superfund Site 9L-4 Area
DATES INCLUDED IN SUMMARY
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77
OSHINSamp Associates Inc
Industrial Hygiene amp Emironmvntal Testing
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Company
LOCATION Salem Acres Superfund Site SL-4 Area
DATES INCLUDED IN SUMMARY J_
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SUMMARIZED BY FOR CASHINS amp ASSOCIATES INC
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CASHINS amp Associates Inc
Industrial Hygifnr amp [nvironmenljl res
SERIOUS HAZARD NOTIFICATION
ISSUED TO REPRESENTING
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PROJECT NAME_ SITE LOCATION
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CISHINS amp Associates Inc
Industrial Hygirne amp Cmimnmtntal Testing
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Company
LOCATION Salem Acres Superfund Site SL-4 Area
DATES INCLUDED IN SUMMARY T
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CASHINSamp Associates Inc
WEEKLY HEALTH amp SA7STT PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Coqpanv
LOCATION Sa^am Acras Super fund 5 jte SL-4 Area
DATES INCLUDED IN SUMMARY bull
11 bdquo mdashbull - ampruzpoundtC4 poundLampu ^6zUT
b( I fa We
FOR CASHINS amp ASSOCIATES INC
53 CAMBRIDGE STREET bull SUTE40I bull BURIJSCTON MA 0803 TfL 61 7-273-908O bull FAX fairo-Jshy
07161996 1658 6179444032 CASHINS S ASSOCIATES PAGE 86
CASHINSamp Associates Inc
MtanW HriHtif A
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT ^ mdash
CLIENT T Ford Company
LOCATION Salem Acraa Suoerfund Sita 5L-4
DATES INCLUDED IN SUMMARY bull
6 03 HL fro- TH4-shy
lt Go
i
tOOf
fo
SUMMARIZED BY FOR CASHINS amp ASSOCIATES INC
55 CAMBRIDGE STREET bullSUITE 201 bull BURllNCTON MA 01803 bull TEL 617-273-9080 bull FAX 617-273-9084
07161996 1650 617944408 CASHING 3 ASSOCIATES PAGE 05
CASHINSamp Associates Inc
fmimnntattl few
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT t T Ford Coimbanv
LOCATION t Salam Acraa Suoarfund Site SL-4 Arlaquoa
DATES INCLUDED IN SUMMARYj pound mdashiffofrshy f
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SUMMARIZ2D BY _ ampampS FOR CASHINS amp ASSOCIATES INC
55 CAMBRIDGE STREET bull SUITE 201 bull BURLINGTON MA 01803 lt TEL 617-273-9080 bull FAX 617-273-9084
CASHIMS amp ASSOCIATES PAGE 04 07161996 1658 6179444032
OVSHINSamp Associates Inc
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Company T
LOCATION Salem AcrM Suoerfund Stta 8L-4 Araa
DATES INCLUDED IN SUMMARY
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SUMMARIZED BY pound FOR CASHINS amp ASSOCIATES INC
55 CAMBRIDGE STREET bull SUITE 201 bull BURUNGTON MA 01803 bull TEL 617-273-9080 bull FAX 617-273-9084
07161996 1658 6179444082 CASHIMS 3 ASSOCIATES PAGE 03
CASHINSamp Associates Inc
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CLIENT T Ford Company t lP ~ ff2-r
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DATES INCLUDED IN SUMMARY
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55 CAMBRIDGE STREET bull SUITE 201 bull 8URUNGTON MA 01803 bull TEL 617-273-9080 bull FAX 617-273-90W
07151996 18 fO 6179444082 CASHINS S ASSOCIATES PAGE 02
CASHINS amp Associates Inc
WBBKLY HEALTH amp SAFETY FLAK COMPLIANCE SUMMARY REPORT
CLIENT T Ford Compapv
LOCATION i Sal am Acrlaquolaquo Suparfund Sita SL-4 Area
DATES INCLUDED IN SUMMARY i bull pound7 mdash
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SXWMARIZ2D BY FOR CASHINS amp ASSOCIATES INC (
55 CAMBRIDGE STREET SUITE 201 bull SURtlNCTON MA 01803 TEL 617-273-9080 bull FAX 61 7-273-9084
- barcode 14732
- barcodetext SEMS Doc ID 14732
![Page 52: SALEM ACRES SUPERFUND SITE SALEM, MA ...The truck loading pa d consisted of a crushed stone are sea t up along the east sid e o f SL-4 adjacent to the access road A. row of concrete](https://reader036.vdocuments.us/reader036/viewer/2022070114/60729b840fec4e6b4d136a16/html5/thumbnails/52.jpg)
OSHINSamp Associates Inc
Industrill Hygiene amp Environnivnljl fating
SITE SPECIFIC amp HAZARD COMMUNICATIONS TRAINING SIGN-IN SHEET
DATE poundLOCATION OF TRAINING
TIME
NAME COMPANY SIGNATURE
j
40 SAUM ST bull LYNNFIELD MA (J1J40 bull TEL 617-2-T 1773 FAX (gtI7 M5-iU7i
CASHINS amp Associates Inc
Industrie Hygitmt amp tnvironmvnlal
SITE SPECIFIC amp HAZARD COMMUNICATIONS TRAINING SIGN-IN SHEET
DATE
LOCATION OF TRAINING
ir bull vr~ TIME - laquo t bullgt
NAME COMPANY SIGNATURE
r_
rd C
lt
40 SALEM ST bull LYNNFIELD MA 01J40 bull TEL 617-245-J77J bull FAX (gtl7--IS4()rj
89111995 1023 6172733(384 CASHINS ASSOCIATES PAGE 01
CASHINS amp Associates inc
Ifxtuitral Hygltne A fnvironmtnltt Tuning
W3SXLY HBALTH amp SAFETY PLAN COMPLIANCE SUMMARY R3PORT
CLIENT T foyd C o m a n
LOCATION gal era Acres Sx^perfund Site 8L-4 Area
DATES INCLUDED IN SUMMARY
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-
SUMMARIZED BY FOR CASHINS amp ASSOCIATES INC
55 CAMBRIDGE STREET bull SUITE 201 bull BURLINGTON MA 01803 laquo TEL 61 -273-9080 bull FAX 67-273-9C84
09111995 1023 6172739084 CASHINS ASSOCIATES PAGE 01
CASHINSamp Associates Inc
Induttrml Hygttnr t Emtroomtnttl Ttstinf
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Fprd Company
LOCATION Salen Acres Suoerfund Site SL-4 Area
DATES INCLUDED IN SUMMARY
000 mdash0
ITr-
^ tcf f
I
SUMMARIZED BY FOR CASHINS 4 ASSOCIATES INC
55 CAMBRIDGE STREET bull SUITE 201 bull BURLINGTON MA 01803 raquo- TEL 6J 7-273-9080 bull FAX 617-273-9084
CASHINS amp Associates Inc
Industrial Hygitnf amp CmimnmenUl Tinting
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Compan
LOCATION Salem Acres Superfund Site SL-4 Area
DATES INCLUDED IN SUMMARY
-amp
I
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bull amppoundf-te
-ampp
4 shy
(4-4
6
SUMMARIZED BY FOR CASHINS amp ASSOCIATES INC
55 CAMBRIDGE STREET SUTE20 bull BLRLINCTON MA 01803 TEL-b l 7-273-9080 bull FAX 61 r-~3-084
CASHING X ASSOCIATES PAGE
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WEEKLY HEALTH amp SAFBTT PLAN COMPLIANCE SUMMARY REPORT
CLIENT ^T Ford Combanv
LOCATION Salam Aerag SL-4
DATES INCLUDED IN SUMMARY
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55 CAMBRIDGE STREET bull SUITE 201 bull SURUNCTON vu 01803 TEL 61 rori-^oao FAX 61 ~ rj
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LOCATION
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CA5HIN3 i AH30CIATES INC
55 CAM8RJDCpound STWET bull SUTTE201 eolaquolNCTONMAOJlaquo03 TIL 6t7shy
07161996 1650 6179444082 CASH INS amp ASSOCIATES PAGE 08
CASHINSamp Associates Inc
Intutttitl Myffcnt t InvtmnmmUt Itnl
WEEKLY HEALTH 6 SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Fortjl Cqjapany
LOCATION Salem Acrlaquoa Superfund Site 9L-4 Area
DATES INCLUDED IN SUMMARY
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SUMMARIZED BY FOR CASKINS amp ASSOCIATES INC
55 CAMBRIDGE STREFT SUITE 201 bull BURUNCTON MA oisoa bull TEL 617-273-9030 bull FAX 6i 7-273-9084
77
OSHINSamp Associates Inc
Industrial Hygiene amp Emironmvntal Testing
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Company
LOCATION Salem Acres Superfund Site SL-4 Area
DATES INCLUDED IN SUMMARY J_
pound0
77
cftf r
SUMMARIZED BY FOR CASHINS amp ASSOCIATES INC
5 CAMBRIDGE STREET bull SUITE JO I bull BURLINGTON MA 01 K03 TEL ltjl 7-J7J-9080 bull FAX b I 7-273-9084
CASHINS amp Associates Inc
Industrial Hygifnr amp [nvironmenljl res
SERIOUS HAZARD NOTIFICATION
ISSUED TO REPRESENTING
ISSUED BY REPRESENTING CASHINS S ASSOCIATES INcT DAY DATE ISSUED O04Xmdash 1 bull-bullmdashbull f P^JT
PROJECT NAME_ SITE LOCATION
THE PURPOSE OF THE FOLLOWING STATEMENT IS TO DOCUMENT THE EXISTENCE OF A CONDITION OR CONCERN WHICH CASHINS amp ASSOCIATES INC BELIEVES WARRANTS IMMEDIATE CORRECTIVE ACTION POSSIBLE SOLUTIONS AND OR CORRECTIVE ACTIONS WILL BE INCLUDED IN THIS NOTIFICATION WHEN POSSIBLE THIS NOTIFICATION IS LIMITED TO SITUATIONS THAT REPRESENT EITHER IMMEDIATE DANGER TO LIFE OR HEALTH CONDITIONS OR PREVIOUSLY IDENTIFIED CHRONIC PROBLEMS THAT UNDERMINE OUR ABILITY TO EFFECTIVELY INSURE COMPLIANCE WITH THE REQUIREMENTS OF THE HEALTH AND SAFETY PLAN
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ACKNOWLEDGEMENT OF ISSUANCE OF NOTIFICATION - NAMECOMPANY ^gt j^f^u^^ CASHINS amp ASSOCINC DATE0 IS
55 CAMBRIDGE STREET bull SUITE 201 bull BURLINGTON MA 01 803 bull TEL 61 7-273-9080 bull FAX fgtl 7-273-9084
CISHINS amp Associates Inc
Industrial Hygirne amp Cmimnmtntal Testing
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Company
LOCATION Salem Acres Superfund Site SL-4 Area
DATES INCLUDED IN SUMMARY T
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SUMMARIZED BY FOR CASHINS amp ASSOCIATES INC
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87161996 1650 6179444882 CASHINS amp ASSOCIATES
CASHINSamp Associates Inc
WEEKLY HEALTH amp SA7STT PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Coqpanv
LOCATION Sa^am Acras Super fund 5 jte SL-4 Area
DATES INCLUDED IN SUMMARY bull
11 bdquo mdashbull - ampruzpoundtC4 poundLampu ^6zUT
b( I fa We
FOR CASHINS amp ASSOCIATES INC
53 CAMBRIDGE STREET bull SUTE40I bull BURIJSCTON MA 0803 TfL 61 7-273-908O bull FAX fairo-Jshy
07161996 1658 6179444032 CASHINS S ASSOCIATES PAGE 86
CASHINSamp Associates Inc
MtanW HriHtif A
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT ^ mdash
CLIENT T Ford Company
LOCATION Salem Acraa Suoerfund Sita 5L-4
DATES INCLUDED IN SUMMARY bull
6 03 HL fro- TH4-shy
lt Go
i
tOOf
fo
SUMMARIZED BY FOR CASHINS amp ASSOCIATES INC
55 CAMBRIDGE STREET bullSUITE 201 bull BURllNCTON MA 01803 bull TEL 617-273-9080 bull FAX 617-273-9084
07161996 1650 617944408 CASHING 3 ASSOCIATES PAGE 05
CASHINSamp Associates Inc
fmimnntattl few
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT t T Ford Coimbanv
LOCATION t Salam Acraa Suoarfund Site SL-4 Arlaquoa
DATES INCLUDED IN SUMMARYj pound mdashiffofrshy f
K (J
-ficuts O
SUMMARIZ2D BY _ ampampS FOR CASHINS amp ASSOCIATES INC
55 CAMBRIDGE STREET bull SUITE 201 bull BURLINGTON MA 01803 lt TEL 617-273-9080 bull FAX 617-273-9084
CASHIMS amp ASSOCIATES PAGE 04 07161996 1658 6179444032
OVSHINSamp Associates Inc
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Company T
LOCATION Salem AcrM Suoerfund Stta 8L-4 Araa
DATES INCLUDED IN SUMMARY
(7
ft ^ 0
SUMMARIZED BY pound FOR CASHINS amp ASSOCIATES INC
55 CAMBRIDGE STREET bull SUITE 201 bull BURUNGTON MA 01803 bull TEL 617-273-9080 bull FAX 617-273-9084
07161996 1658 6179444082 CASHIMS 3 ASSOCIATES PAGE 03
CASHINSamp Associates Inc
ndurtrW Hrtnm t
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT ^
CLIENT T Ford Company t lP ~ ff2-r
LOCATION Sal era Acraa Suplaquorfund Sj-ta 8L-4 Araa
DATES INCLUDED IN SUMMARY
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SUMMARIZED BY FOR CASMINS amp ASSOCIATES INC
55 CAMBRIDGE STREET bull SUITE 201 bull 8URUNGTON MA 01803 bull TEL 617-273-9080 bull FAX 617-273-90W
07151996 18 fO 6179444082 CASHINS S ASSOCIATES PAGE 02
CASHINS amp Associates Inc
WBBKLY HEALTH amp SAFETY FLAK COMPLIANCE SUMMARY REPORT
CLIENT T Ford Compapv
LOCATION i Sal am Acrlaquolaquo Suparfund Sita SL-4 Area
DATES INCLUDED IN SUMMARY i bull pound7 mdash
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SXWMARIZ2D BY FOR CASHINS amp ASSOCIATES INC (
55 CAMBRIDGE STREET SUITE 201 bull SURtlNCTON MA 01803 TEL 617-273-9080 bull FAX 61 7-273-9084
- barcode 14732
- barcodetext SEMS Doc ID 14732
![Page 53: SALEM ACRES SUPERFUND SITE SALEM, MA ...The truck loading pa d consisted of a crushed stone are sea t up along the east sid e o f SL-4 adjacent to the access road A. row of concrete](https://reader036.vdocuments.us/reader036/viewer/2022070114/60729b840fec4e6b4d136a16/html5/thumbnails/53.jpg)
CASHINS amp Associates Inc
Industrie Hygitmt amp tnvironmvnlal
SITE SPECIFIC amp HAZARD COMMUNICATIONS TRAINING SIGN-IN SHEET
DATE
LOCATION OF TRAINING
ir bull vr~ TIME - laquo t bullgt
NAME COMPANY SIGNATURE
r_
rd C
lt
40 SALEM ST bull LYNNFIELD MA 01J40 bull TEL 617-245-J77J bull FAX (gtl7--IS4()rj
89111995 1023 6172733(384 CASHINS ASSOCIATES PAGE 01
CASHINS amp Associates inc
Ifxtuitral Hygltne A fnvironmtnltt Tuning
W3SXLY HBALTH amp SAFETY PLAN COMPLIANCE SUMMARY R3PORT
CLIENT T foyd C o m a n
LOCATION gal era Acres Sx^perfund Site 8L-4 Area
DATES INCLUDED IN SUMMARY
toe
-
SUMMARIZED BY FOR CASHINS amp ASSOCIATES INC
55 CAMBRIDGE STREET bull SUITE 201 bull BURLINGTON MA 01803 laquo TEL 61 -273-9080 bull FAX 67-273-9C84
09111995 1023 6172739084 CASHINS ASSOCIATES PAGE 01
CASHINSamp Associates Inc
Induttrml Hygttnr t Emtroomtnttl Ttstinf
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Fprd Company
LOCATION Salen Acres Suoerfund Site SL-4 Area
DATES INCLUDED IN SUMMARY
000 mdash0
ITr-
^ tcf f
I
SUMMARIZED BY FOR CASHINS 4 ASSOCIATES INC
55 CAMBRIDGE STREET bull SUITE 201 bull BURLINGTON MA 01803 raquo- TEL 6J 7-273-9080 bull FAX 617-273-9084
CASHINS amp Associates Inc
Industrial Hygitnf amp CmimnmenUl Tinting
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Compan
LOCATION Salem Acres Superfund Site SL-4 Area
DATES INCLUDED IN SUMMARY
-amp
I
tu bull lts fffr-t TC mdash
bull amppoundf-te
-ampp
4 shy
(4-4
6
SUMMARIZED BY FOR CASHINS amp ASSOCIATES INC
55 CAMBRIDGE STREET SUTE20 bull BLRLINCTON MA 01803 TEL-b l 7-273-9080 bull FAX 61 r-~3-084
CASHING X ASSOCIATES PAGE
1C n -044408shy07161336 1650 61 344408shy
CASHINSamp Associates Inc
WEEKLY HEALTH amp SAFBTT PLAN COMPLIANCE SUMMARY REPORT
CLIENT ^T Ford Combanv
LOCATION Salam Aerag SL-4
DATES INCLUDED IN SUMMARY
- ^ ^
MS
tct
W
CCo c 77shy
SUMMARIZED BY FOR CASHINS amp ASSOCIATES INC
55 CAMBRIDGE STREET bull SUITE 201 bull SURUNCTON vu 01803 TEL 61 rori-^oao FAX 61 ~ rj
07161996 1650 6179444082 CASHI MS amp ASSOCIATES PAGE 10
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CLIENT
LOCATION
DATES INCLUDED IN BUNKARY)
CA5HIN3 i AH30CIATES INC
55 CAM8RJDCpound STWET bull SUTTE201 eolaquolNCTONMAOJlaquo03 TIL 6t7shy
07161996 1650 6179444082 CASH INS amp ASSOCIATES PAGE 08
CASHINSamp Associates Inc
Intutttitl Myffcnt t InvtmnmmUt Itnl
WEEKLY HEALTH 6 SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Fortjl Cqjapany
LOCATION Salem Acrlaquoa Superfund Site 9L-4 Area
DATES INCLUDED IN SUMMARY
s
O7 shy^
ampspounde
(TTT- J
SUMMARIZED BY FOR CASKINS amp ASSOCIATES INC
55 CAMBRIDGE STREFT SUITE 201 bull BURUNCTON MA oisoa bull TEL 617-273-9030 bull FAX 6i 7-273-9084
77
OSHINSamp Associates Inc
Industrial Hygiene amp Emironmvntal Testing
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Company
LOCATION Salem Acres Superfund Site SL-4 Area
DATES INCLUDED IN SUMMARY J_
pound0
77
cftf r
SUMMARIZED BY FOR CASHINS amp ASSOCIATES INC
5 CAMBRIDGE STREET bull SUITE JO I bull BURLINGTON MA 01 K03 TEL ltjl 7-J7J-9080 bull FAX b I 7-273-9084
CASHINS amp Associates Inc
Industrial Hygifnr amp [nvironmenljl res
SERIOUS HAZARD NOTIFICATION
ISSUED TO REPRESENTING
ISSUED BY REPRESENTING CASHINS S ASSOCIATES INcT DAY DATE ISSUED O04Xmdash 1 bull-bullmdashbull f P^JT
PROJECT NAME_ SITE LOCATION
THE PURPOSE OF THE FOLLOWING STATEMENT IS TO DOCUMENT THE EXISTENCE OF A CONDITION OR CONCERN WHICH CASHINS amp ASSOCIATES INC BELIEVES WARRANTS IMMEDIATE CORRECTIVE ACTION POSSIBLE SOLUTIONS AND OR CORRECTIVE ACTIONS WILL BE INCLUDED IN THIS NOTIFICATION WHEN POSSIBLE THIS NOTIFICATION IS LIMITED TO SITUATIONS THAT REPRESENT EITHER IMMEDIATE DANGER TO LIFE OR HEALTH CONDITIONS OR PREVIOUSLY IDENTIFIED CHRONIC PROBLEMS THAT UNDERMINE OUR ABILITY TO EFFECTIVELY INSURE COMPLIANCE WITH THE REQUIREMENTS OF THE HEALTH AND SAFETY PLAN
0
TLc ic^ricj^r
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ACKNOWLEDGEMENT OF RECEIPT OF NOTIFICATION NAMECOMPANY DATE
ACKNOWLEDGEMENT OF ISSUANCE OF NOTIFICATION - NAMECOMPANY ^gt j^f^u^^ CASHINS amp ASSOCINC DATE0 IS
55 CAMBRIDGE STREET bull SUITE 201 bull BURLINGTON MA 01 803 bull TEL 61 7-273-9080 bull FAX fgtl 7-273-9084
CISHINS amp Associates Inc
Industrial Hygirne amp Cmimnmtntal Testing
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Company
LOCATION Salem Acres Superfund Site SL-4 Area
DATES INCLUDED IN SUMMARY T
(5 f0^ degT a
pound btU-pcfa _ J _
- ltpfampo
(J -gt ft
SUMMARIZED BY FOR CASHINS amp ASSOCIATES INC
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87161996 1650 6179444882 CASHINS amp ASSOCIATES
CASHINSamp Associates Inc
WEEKLY HEALTH amp SA7STT PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Coqpanv
LOCATION Sa^am Acras Super fund 5 jte SL-4 Area
DATES INCLUDED IN SUMMARY bull
11 bdquo mdashbull - ampruzpoundtC4 poundLampu ^6zUT
b( I fa We
FOR CASHINS amp ASSOCIATES INC
53 CAMBRIDGE STREET bull SUTE40I bull BURIJSCTON MA 0803 TfL 61 7-273-908O bull FAX fairo-Jshy
07161996 1658 6179444032 CASHINS S ASSOCIATES PAGE 86
CASHINSamp Associates Inc
MtanW HriHtif A
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT ^ mdash
CLIENT T Ford Company
LOCATION Salem Acraa Suoerfund Sita 5L-4
DATES INCLUDED IN SUMMARY bull
6 03 HL fro- TH4-shy
lt Go
i
tOOf
fo
SUMMARIZED BY FOR CASHINS amp ASSOCIATES INC
55 CAMBRIDGE STREET bullSUITE 201 bull BURllNCTON MA 01803 bull TEL 617-273-9080 bull FAX 617-273-9084
07161996 1650 617944408 CASHING 3 ASSOCIATES PAGE 05
CASHINSamp Associates Inc
fmimnntattl few
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT t T Ford Coimbanv
LOCATION t Salam Acraa Suoarfund Site SL-4 Arlaquoa
DATES INCLUDED IN SUMMARYj pound mdashiffofrshy f
K (J
-ficuts O
SUMMARIZ2D BY _ ampampS FOR CASHINS amp ASSOCIATES INC
55 CAMBRIDGE STREET bull SUITE 201 bull BURLINGTON MA 01803 lt TEL 617-273-9080 bull FAX 617-273-9084
CASHIMS amp ASSOCIATES PAGE 04 07161996 1658 6179444032
OVSHINSamp Associates Inc
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Company T
LOCATION Salem AcrM Suoerfund Stta 8L-4 Araa
DATES INCLUDED IN SUMMARY
(7
ft ^ 0
SUMMARIZED BY pound FOR CASHINS amp ASSOCIATES INC
55 CAMBRIDGE STREET bull SUITE 201 bull BURUNGTON MA 01803 bull TEL 617-273-9080 bull FAX 617-273-9084
07161996 1658 6179444082 CASHIMS 3 ASSOCIATES PAGE 03
CASHINSamp Associates Inc
ndurtrW Hrtnm t
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT ^
CLIENT T Ford Company t lP ~ ff2-r
LOCATION Sal era Acraa Suplaquorfund Sj-ta 8L-4 Araa
DATES INCLUDED IN SUMMARY
if
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SUMMARIZED BY FOR CASMINS amp ASSOCIATES INC
55 CAMBRIDGE STREET bull SUITE 201 bull 8URUNGTON MA 01803 bull TEL 617-273-9080 bull FAX 617-273-90W
07151996 18 fO 6179444082 CASHINS S ASSOCIATES PAGE 02
CASHINS amp Associates Inc
WBBKLY HEALTH amp SAFETY FLAK COMPLIANCE SUMMARY REPORT
CLIENT T Ford Compapv
LOCATION i Sal am Acrlaquolaquo Suparfund Sita SL-4 Area
DATES INCLUDED IN SUMMARY i bull pound7 mdash
A 0-3 - A)
SXWMARIZ2D BY FOR CASHINS amp ASSOCIATES INC (
55 CAMBRIDGE STREET SUITE 201 bull SURtlNCTON MA 01803 TEL 617-273-9080 bull FAX 61 7-273-9084
- barcode 14732
- barcodetext SEMS Doc ID 14732
![Page 54: SALEM ACRES SUPERFUND SITE SALEM, MA ...The truck loading pa d consisted of a crushed stone are sea t up along the east sid e o f SL-4 adjacent to the access road A. row of concrete](https://reader036.vdocuments.us/reader036/viewer/2022070114/60729b840fec4e6b4d136a16/html5/thumbnails/54.jpg)
89111995 1023 6172733(384 CASHINS ASSOCIATES PAGE 01
CASHINS amp Associates inc
Ifxtuitral Hygltne A fnvironmtnltt Tuning
W3SXLY HBALTH amp SAFETY PLAN COMPLIANCE SUMMARY R3PORT
CLIENT T foyd C o m a n
LOCATION gal era Acres Sx^perfund Site 8L-4 Area
DATES INCLUDED IN SUMMARY
toe
-
SUMMARIZED BY FOR CASHINS amp ASSOCIATES INC
55 CAMBRIDGE STREET bull SUITE 201 bull BURLINGTON MA 01803 laquo TEL 61 -273-9080 bull FAX 67-273-9C84
09111995 1023 6172739084 CASHINS ASSOCIATES PAGE 01
CASHINSamp Associates Inc
Induttrml Hygttnr t Emtroomtnttl Ttstinf
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Fprd Company
LOCATION Salen Acres Suoerfund Site SL-4 Area
DATES INCLUDED IN SUMMARY
000 mdash0
ITr-
^ tcf f
I
SUMMARIZED BY FOR CASHINS 4 ASSOCIATES INC
55 CAMBRIDGE STREET bull SUITE 201 bull BURLINGTON MA 01803 raquo- TEL 6J 7-273-9080 bull FAX 617-273-9084
CASHINS amp Associates Inc
Industrial Hygitnf amp CmimnmenUl Tinting
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Compan
LOCATION Salem Acres Superfund Site SL-4 Area
DATES INCLUDED IN SUMMARY
-amp
I
tu bull lts fffr-t TC mdash
bull amppoundf-te
-ampp
4 shy
(4-4
6
SUMMARIZED BY FOR CASHINS amp ASSOCIATES INC
55 CAMBRIDGE STREET SUTE20 bull BLRLINCTON MA 01803 TEL-b l 7-273-9080 bull FAX 61 r-~3-084
CASHING X ASSOCIATES PAGE
1C n -044408shy07161336 1650 61 344408shy
CASHINSamp Associates Inc
WEEKLY HEALTH amp SAFBTT PLAN COMPLIANCE SUMMARY REPORT
CLIENT ^T Ford Combanv
LOCATION Salam Aerag SL-4
DATES INCLUDED IN SUMMARY
- ^ ^
MS
tct
W
CCo c 77shy
SUMMARIZED BY FOR CASHINS amp ASSOCIATES INC
55 CAMBRIDGE STREET bull SUITE 201 bull SURUNCTON vu 01803 TEL 61 rori-^oao FAX 61 ~ rj
07161996 1650 6179444082 CASHI MS amp ASSOCIATES PAGE 10
-bulli wtAxi 4ll-fJSt4bf SZshy
^ - ^ bull bull Vl bull bull shy bullbullbull -VdUMSW^
bullv^F4GE8lamplaquoshybullbull-bull vltfrjy rvs 7v
C4SHINSamp Araquood^Ktoc
W8ZKLY B2ALTB ft PLWf COMPL1ANCS SUHXAJIT
CLIENT
LOCATION
DATES INCLUDED IN BUNKARY)
CA5HIN3 i AH30CIATES INC
55 CAM8RJDCpound STWET bull SUTTE201 eolaquolNCTONMAOJlaquo03 TIL 6t7shy
07161996 1650 6179444082 CASH INS amp ASSOCIATES PAGE 08
CASHINSamp Associates Inc
Intutttitl Myffcnt t InvtmnmmUt Itnl
WEEKLY HEALTH 6 SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Fortjl Cqjapany
LOCATION Salem Acrlaquoa Superfund Site 9L-4 Area
DATES INCLUDED IN SUMMARY
s
O7 shy^
ampspounde
(TTT- J
SUMMARIZED BY FOR CASKINS amp ASSOCIATES INC
55 CAMBRIDGE STREFT SUITE 201 bull BURUNCTON MA oisoa bull TEL 617-273-9030 bull FAX 6i 7-273-9084
77
OSHINSamp Associates Inc
Industrial Hygiene amp Emironmvntal Testing
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Company
LOCATION Salem Acres Superfund Site SL-4 Area
DATES INCLUDED IN SUMMARY J_
pound0
77
cftf r
SUMMARIZED BY FOR CASHINS amp ASSOCIATES INC
5 CAMBRIDGE STREET bull SUITE JO I bull BURLINGTON MA 01 K03 TEL ltjl 7-J7J-9080 bull FAX b I 7-273-9084
CASHINS amp Associates Inc
Industrial Hygifnr amp [nvironmenljl res
SERIOUS HAZARD NOTIFICATION
ISSUED TO REPRESENTING
ISSUED BY REPRESENTING CASHINS S ASSOCIATES INcT DAY DATE ISSUED O04Xmdash 1 bull-bullmdashbull f P^JT
PROJECT NAME_ SITE LOCATION
THE PURPOSE OF THE FOLLOWING STATEMENT IS TO DOCUMENT THE EXISTENCE OF A CONDITION OR CONCERN WHICH CASHINS amp ASSOCIATES INC BELIEVES WARRANTS IMMEDIATE CORRECTIVE ACTION POSSIBLE SOLUTIONS AND OR CORRECTIVE ACTIONS WILL BE INCLUDED IN THIS NOTIFICATION WHEN POSSIBLE THIS NOTIFICATION IS LIMITED TO SITUATIONS THAT REPRESENT EITHER IMMEDIATE DANGER TO LIFE OR HEALTH CONDITIONS OR PREVIOUSLY IDENTIFIED CHRONIC PROBLEMS THAT UNDERMINE OUR ABILITY TO EFFECTIVELY INSURE COMPLIANCE WITH THE REQUIREMENTS OF THE HEALTH AND SAFETY PLAN
0
TLc ic^ricj^r
e fv
f P U_ -L AM - fshy V mdash [T T
ACKNOWLEDGEMENT OF RECEIPT OF NOTIFICATION NAMECOMPANY DATE
ACKNOWLEDGEMENT OF ISSUANCE OF NOTIFICATION - NAMECOMPANY ^gt j^f^u^^ CASHINS amp ASSOCINC DATE0 IS
55 CAMBRIDGE STREET bull SUITE 201 bull BURLINGTON MA 01 803 bull TEL 61 7-273-9080 bull FAX fgtl 7-273-9084
CISHINS amp Associates Inc
Industrial Hygirne amp Cmimnmtntal Testing
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Company
LOCATION Salem Acres Superfund Site SL-4 Area
DATES INCLUDED IN SUMMARY T
(5 f0^ degT a
pound btU-pcfa _ J _
- ltpfampo
(J -gt ft
SUMMARIZED BY FOR CASHINS amp ASSOCIATES INC
f a 7 ) ) F A X i gt I 7-273-^)84
87161996 1650 6179444882 CASHINS amp ASSOCIATES
CASHINSamp Associates Inc
WEEKLY HEALTH amp SA7STT PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Coqpanv
LOCATION Sa^am Acras Super fund 5 jte SL-4 Area
DATES INCLUDED IN SUMMARY bull
11 bdquo mdashbull - ampruzpoundtC4 poundLampu ^6zUT
b( I fa We
FOR CASHINS amp ASSOCIATES INC
53 CAMBRIDGE STREET bull SUTE40I bull BURIJSCTON MA 0803 TfL 61 7-273-908O bull FAX fairo-Jshy
07161996 1658 6179444032 CASHINS S ASSOCIATES PAGE 86
CASHINSamp Associates Inc
MtanW HriHtif A
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT ^ mdash
CLIENT T Ford Company
LOCATION Salem Acraa Suoerfund Sita 5L-4
DATES INCLUDED IN SUMMARY bull
6 03 HL fro- TH4-shy
lt Go
i
tOOf
fo
SUMMARIZED BY FOR CASHINS amp ASSOCIATES INC
55 CAMBRIDGE STREET bullSUITE 201 bull BURllNCTON MA 01803 bull TEL 617-273-9080 bull FAX 617-273-9084
07161996 1650 617944408 CASHING 3 ASSOCIATES PAGE 05
CASHINSamp Associates Inc
fmimnntattl few
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT t T Ford Coimbanv
LOCATION t Salam Acraa Suoarfund Site SL-4 Arlaquoa
DATES INCLUDED IN SUMMARYj pound mdashiffofrshy f
K (J
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SUMMARIZ2D BY _ ampampS FOR CASHINS amp ASSOCIATES INC
55 CAMBRIDGE STREET bull SUITE 201 bull BURLINGTON MA 01803 lt TEL 617-273-9080 bull FAX 617-273-9084
CASHIMS amp ASSOCIATES PAGE 04 07161996 1658 6179444032
OVSHINSamp Associates Inc
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Company T
LOCATION Salem AcrM Suoerfund Stta 8L-4 Araa
DATES INCLUDED IN SUMMARY
(7
ft ^ 0
SUMMARIZED BY pound FOR CASHINS amp ASSOCIATES INC
55 CAMBRIDGE STREET bull SUITE 201 bull BURUNGTON MA 01803 bull TEL 617-273-9080 bull FAX 617-273-9084
07161996 1658 6179444082 CASHIMS 3 ASSOCIATES PAGE 03
CASHINSamp Associates Inc
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CLIENT T Ford Company t lP ~ ff2-r
LOCATION Sal era Acraa Suplaquorfund Sj-ta 8L-4 Araa
DATES INCLUDED IN SUMMARY
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55 CAMBRIDGE STREET bull SUITE 201 bull 8URUNGTON MA 01803 bull TEL 617-273-9080 bull FAX 617-273-90W
07151996 18 fO 6179444082 CASHINS S ASSOCIATES PAGE 02
CASHINS amp Associates Inc
WBBKLY HEALTH amp SAFETY FLAK COMPLIANCE SUMMARY REPORT
CLIENT T Ford Compapv
LOCATION i Sal am Acrlaquolaquo Suparfund Sita SL-4 Area
DATES INCLUDED IN SUMMARY i bull pound7 mdash
A 0-3 - A)
SXWMARIZ2D BY FOR CASHINS amp ASSOCIATES INC (
55 CAMBRIDGE STREET SUITE 201 bull SURtlNCTON MA 01803 TEL 617-273-9080 bull FAX 61 7-273-9084
- barcode 14732
- barcodetext SEMS Doc ID 14732
![Page 55: SALEM ACRES SUPERFUND SITE SALEM, MA ...The truck loading pa d consisted of a crushed stone are sea t up along the east sid e o f SL-4 adjacent to the access road A. row of concrete](https://reader036.vdocuments.us/reader036/viewer/2022070114/60729b840fec4e6b4d136a16/html5/thumbnails/55.jpg)
09111995 1023 6172739084 CASHINS ASSOCIATES PAGE 01
CASHINSamp Associates Inc
Induttrml Hygttnr t Emtroomtnttl Ttstinf
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Fprd Company
LOCATION Salen Acres Suoerfund Site SL-4 Area
DATES INCLUDED IN SUMMARY
000 mdash0
ITr-
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SUMMARIZED BY FOR CASHINS 4 ASSOCIATES INC
55 CAMBRIDGE STREET bull SUITE 201 bull BURLINGTON MA 01803 raquo- TEL 6J 7-273-9080 bull FAX 617-273-9084
CASHINS amp Associates Inc
Industrial Hygitnf amp CmimnmenUl Tinting
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Compan
LOCATION Salem Acres Superfund Site SL-4 Area
DATES INCLUDED IN SUMMARY
-amp
I
tu bull lts fffr-t TC mdash
bull amppoundf-te
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4 shy
(4-4
6
SUMMARIZED BY FOR CASHINS amp ASSOCIATES INC
55 CAMBRIDGE STREET SUTE20 bull BLRLINCTON MA 01803 TEL-b l 7-273-9080 bull FAX 61 r-~3-084
CASHING X ASSOCIATES PAGE
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WEEKLY HEALTH amp SAFBTT PLAN COMPLIANCE SUMMARY REPORT
CLIENT ^T Ford Combanv
LOCATION Salam Aerag SL-4
DATES INCLUDED IN SUMMARY
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55 CAMBRIDGE STREET bull SUITE 201 bull SURUNCTON vu 01803 TEL 61 rori-^oao FAX 61 ~ rj
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55 CAM8RJDCpound STWET bull SUTTE201 eolaquolNCTONMAOJlaquo03 TIL 6t7shy
07161996 1650 6179444082 CASH INS amp ASSOCIATES PAGE 08
CASHINSamp Associates Inc
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WEEKLY HEALTH 6 SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Fortjl Cqjapany
LOCATION Salem Acrlaquoa Superfund Site 9L-4 Area
DATES INCLUDED IN SUMMARY
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55 CAMBRIDGE STREFT SUITE 201 bull BURUNCTON MA oisoa bull TEL 617-273-9030 bull FAX 6i 7-273-9084
77
OSHINSamp Associates Inc
Industrial Hygiene amp Emironmvntal Testing
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Company
LOCATION Salem Acres Superfund Site SL-4 Area
DATES INCLUDED IN SUMMARY J_
pound0
77
cftf r
SUMMARIZED BY FOR CASHINS amp ASSOCIATES INC
5 CAMBRIDGE STREET bull SUITE JO I bull BURLINGTON MA 01 K03 TEL ltjl 7-J7J-9080 bull FAX b I 7-273-9084
CASHINS amp Associates Inc
Industrial Hygifnr amp [nvironmenljl res
SERIOUS HAZARD NOTIFICATION
ISSUED TO REPRESENTING
ISSUED BY REPRESENTING CASHINS S ASSOCIATES INcT DAY DATE ISSUED O04Xmdash 1 bull-bullmdashbull f P^JT
PROJECT NAME_ SITE LOCATION
THE PURPOSE OF THE FOLLOWING STATEMENT IS TO DOCUMENT THE EXISTENCE OF A CONDITION OR CONCERN WHICH CASHINS amp ASSOCIATES INC BELIEVES WARRANTS IMMEDIATE CORRECTIVE ACTION POSSIBLE SOLUTIONS AND OR CORRECTIVE ACTIONS WILL BE INCLUDED IN THIS NOTIFICATION WHEN POSSIBLE THIS NOTIFICATION IS LIMITED TO SITUATIONS THAT REPRESENT EITHER IMMEDIATE DANGER TO LIFE OR HEALTH CONDITIONS OR PREVIOUSLY IDENTIFIED CHRONIC PROBLEMS THAT UNDERMINE OUR ABILITY TO EFFECTIVELY INSURE COMPLIANCE WITH THE REQUIREMENTS OF THE HEALTH AND SAFETY PLAN
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55 CAMBRIDGE STREET bull SUITE 201 bull BURLINGTON MA 01 803 bull TEL 61 7-273-9080 bull FAX fgtl 7-273-9084
CISHINS amp Associates Inc
Industrial Hygirne amp Cmimnmtntal Testing
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Company
LOCATION Salem Acres Superfund Site SL-4 Area
DATES INCLUDED IN SUMMARY T
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SUMMARIZED BY FOR CASHINS amp ASSOCIATES INC
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87161996 1650 6179444882 CASHINS amp ASSOCIATES
CASHINSamp Associates Inc
WEEKLY HEALTH amp SA7STT PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Coqpanv
LOCATION Sa^am Acras Super fund 5 jte SL-4 Area
DATES INCLUDED IN SUMMARY bull
11 bdquo mdashbull - ampruzpoundtC4 poundLampu ^6zUT
b( I fa We
FOR CASHINS amp ASSOCIATES INC
53 CAMBRIDGE STREET bull SUTE40I bull BURIJSCTON MA 0803 TfL 61 7-273-908O bull FAX fairo-Jshy
07161996 1658 6179444032 CASHINS S ASSOCIATES PAGE 86
CASHINSamp Associates Inc
MtanW HriHtif A
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT ^ mdash
CLIENT T Ford Company
LOCATION Salem Acraa Suoerfund Sita 5L-4
DATES INCLUDED IN SUMMARY bull
6 03 HL fro- TH4-shy
lt Go
i
tOOf
fo
SUMMARIZED BY FOR CASHINS amp ASSOCIATES INC
55 CAMBRIDGE STREET bullSUITE 201 bull BURllNCTON MA 01803 bull TEL 617-273-9080 bull FAX 617-273-9084
07161996 1650 617944408 CASHING 3 ASSOCIATES PAGE 05
CASHINSamp Associates Inc
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WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT t T Ford Coimbanv
LOCATION t Salam Acraa Suoarfund Site SL-4 Arlaquoa
DATES INCLUDED IN SUMMARYj pound mdashiffofrshy f
K (J
-ficuts O
SUMMARIZ2D BY _ ampampS FOR CASHINS amp ASSOCIATES INC
55 CAMBRIDGE STREET bull SUITE 201 bull BURLINGTON MA 01803 lt TEL 617-273-9080 bull FAX 617-273-9084
CASHIMS amp ASSOCIATES PAGE 04 07161996 1658 6179444032
OVSHINSamp Associates Inc
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Company T
LOCATION Salem AcrM Suoerfund Stta 8L-4 Araa
DATES INCLUDED IN SUMMARY
(7
ft ^ 0
SUMMARIZED BY pound FOR CASHINS amp ASSOCIATES INC
55 CAMBRIDGE STREET bull SUITE 201 bull BURUNGTON MA 01803 bull TEL 617-273-9080 bull FAX 617-273-9084
07161996 1658 6179444082 CASHIMS 3 ASSOCIATES PAGE 03
CASHINSamp Associates Inc
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WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT ^
CLIENT T Ford Company t lP ~ ff2-r
LOCATION Sal era Acraa Suplaquorfund Sj-ta 8L-4 Araa
DATES INCLUDED IN SUMMARY
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55 CAMBRIDGE STREET bull SUITE 201 bull 8URUNGTON MA 01803 bull TEL 617-273-9080 bull FAX 617-273-90W
07151996 18 fO 6179444082 CASHINS S ASSOCIATES PAGE 02
CASHINS amp Associates Inc
WBBKLY HEALTH amp SAFETY FLAK COMPLIANCE SUMMARY REPORT
CLIENT T Ford Compapv
LOCATION i Sal am Acrlaquolaquo Suparfund Sita SL-4 Area
DATES INCLUDED IN SUMMARY i bull pound7 mdash
A 0-3 - A)
SXWMARIZ2D BY FOR CASHINS amp ASSOCIATES INC (
55 CAMBRIDGE STREET SUITE 201 bull SURtlNCTON MA 01803 TEL 617-273-9080 bull FAX 61 7-273-9084
- barcode 14732
- barcodetext SEMS Doc ID 14732
![Page 56: SALEM ACRES SUPERFUND SITE SALEM, MA ...The truck loading pa d consisted of a crushed stone are sea t up along the east sid e o f SL-4 adjacent to the access road A. row of concrete](https://reader036.vdocuments.us/reader036/viewer/2022070114/60729b840fec4e6b4d136a16/html5/thumbnails/56.jpg)
CASHINS amp Associates Inc
Industrial Hygitnf amp CmimnmenUl Tinting
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Compan
LOCATION Salem Acres Superfund Site SL-4 Area
DATES INCLUDED IN SUMMARY
-amp
I
tu bull lts fffr-t TC mdash
bull amppoundf-te
-ampp
4 shy
(4-4
6
SUMMARIZED BY FOR CASHINS amp ASSOCIATES INC
55 CAMBRIDGE STREET SUTE20 bull BLRLINCTON MA 01803 TEL-b l 7-273-9080 bull FAX 61 r-~3-084
CASHING X ASSOCIATES PAGE
1C n -044408shy07161336 1650 61 344408shy
CASHINSamp Associates Inc
WEEKLY HEALTH amp SAFBTT PLAN COMPLIANCE SUMMARY REPORT
CLIENT ^T Ford Combanv
LOCATION Salam Aerag SL-4
DATES INCLUDED IN SUMMARY
- ^ ^
MS
tct
W
CCo c 77shy
SUMMARIZED BY FOR CASHINS amp ASSOCIATES INC
55 CAMBRIDGE STREET bull SUITE 201 bull SURUNCTON vu 01803 TEL 61 rori-^oao FAX 61 ~ rj
07161996 1650 6179444082 CASHI MS amp ASSOCIATES PAGE 10
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CA5HIN3 i AH30CIATES INC
55 CAM8RJDCpound STWET bull SUTTE201 eolaquolNCTONMAOJlaquo03 TIL 6t7shy
07161996 1650 6179444082 CASH INS amp ASSOCIATES PAGE 08
CASHINSamp Associates Inc
Intutttitl Myffcnt t InvtmnmmUt Itnl
WEEKLY HEALTH 6 SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Fortjl Cqjapany
LOCATION Salem Acrlaquoa Superfund Site 9L-4 Area
DATES INCLUDED IN SUMMARY
s
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ampspounde
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SUMMARIZED BY FOR CASKINS amp ASSOCIATES INC
55 CAMBRIDGE STREFT SUITE 201 bull BURUNCTON MA oisoa bull TEL 617-273-9030 bull FAX 6i 7-273-9084
77
OSHINSamp Associates Inc
Industrial Hygiene amp Emironmvntal Testing
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Company
LOCATION Salem Acres Superfund Site SL-4 Area
DATES INCLUDED IN SUMMARY J_
pound0
77
cftf r
SUMMARIZED BY FOR CASHINS amp ASSOCIATES INC
5 CAMBRIDGE STREET bull SUITE JO I bull BURLINGTON MA 01 K03 TEL ltjl 7-J7J-9080 bull FAX b I 7-273-9084
CASHINS amp Associates Inc
Industrial Hygifnr amp [nvironmenljl res
SERIOUS HAZARD NOTIFICATION
ISSUED TO REPRESENTING
ISSUED BY REPRESENTING CASHINS S ASSOCIATES INcT DAY DATE ISSUED O04Xmdash 1 bull-bullmdashbull f P^JT
PROJECT NAME_ SITE LOCATION
THE PURPOSE OF THE FOLLOWING STATEMENT IS TO DOCUMENT THE EXISTENCE OF A CONDITION OR CONCERN WHICH CASHINS amp ASSOCIATES INC BELIEVES WARRANTS IMMEDIATE CORRECTIVE ACTION POSSIBLE SOLUTIONS AND OR CORRECTIVE ACTIONS WILL BE INCLUDED IN THIS NOTIFICATION WHEN POSSIBLE THIS NOTIFICATION IS LIMITED TO SITUATIONS THAT REPRESENT EITHER IMMEDIATE DANGER TO LIFE OR HEALTH CONDITIONS OR PREVIOUSLY IDENTIFIED CHRONIC PROBLEMS THAT UNDERMINE OUR ABILITY TO EFFECTIVELY INSURE COMPLIANCE WITH THE REQUIREMENTS OF THE HEALTH AND SAFETY PLAN
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55 CAMBRIDGE STREET bull SUITE 201 bull BURLINGTON MA 01 803 bull TEL 61 7-273-9080 bull FAX fgtl 7-273-9084
CISHINS amp Associates Inc
Industrial Hygirne amp Cmimnmtntal Testing
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Company
LOCATION Salem Acres Superfund Site SL-4 Area
DATES INCLUDED IN SUMMARY T
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SUMMARIZED BY FOR CASHINS amp ASSOCIATES INC
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87161996 1650 6179444882 CASHINS amp ASSOCIATES
CASHINSamp Associates Inc
WEEKLY HEALTH amp SA7STT PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Coqpanv
LOCATION Sa^am Acras Super fund 5 jte SL-4 Area
DATES INCLUDED IN SUMMARY bull
11 bdquo mdashbull - ampruzpoundtC4 poundLampu ^6zUT
b( I fa We
FOR CASHINS amp ASSOCIATES INC
53 CAMBRIDGE STREET bull SUTE40I bull BURIJSCTON MA 0803 TfL 61 7-273-908O bull FAX fairo-Jshy
07161996 1658 6179444032 CASHINS S ASSOCIATES PAGE 86
CASHINSamp Associates Inc
MtanW HriHtif A
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT ^ mdash
CLIENT T Ford Company
LOCATION Salem Acraa Suoerfund Sita 5L-4
DATES INCLUDED IN SUMMARY bull
6 03 HL fro- TH4-shy
lt Go
i
tOOf
fo
SUMMARIZED BY FOR CASHINS amp ASSOCIATES INC
55 CAMBRIDGE STREET bullSUITE 201 bull BURllNCTON MA 01803 bull TEL 617-273-9080 bull FAX 617-273-9084
07161996 1650 617944408 CASHING 3 ASSOCIATES PAGE 05
CASHINSamp Associates Inc
fmimnntattl few
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT t T Ford Coimbanv
LOCATION t Salam Acraa Suoarfund Site SL-4 Arlaquoa
DATES INCLUDED IN SUMMARYj pound mdashiffofrshy f
K (J
-ficuts O
SUMMARIZ2D BY _ ampampS FOR CASHINS amp ASSOCIATES INC
55 CAMBRIDGE STREET bull SUITE 201 bull BURLINGTON MA 01803 lt TEL 617-273-9080 bull FAX 617-273-9084
CASHIMS amp ASSOCIATES PAGE 04 07161996 1658 6179444032
OVSHINSamp Associates Inc
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Company T
LOCATION Salem AcrM Suoerfund Stta 8L-4 Araa
DATES INCLUDED IN SUMMARY
(7
ft ^ 0
SUMMARIZED BY pound FOR CASHINS amp ASSOCIATES INC
55 CAMBRIDGE STREET bull SUITE 201 bull BURUNGTON MA 01803 bull TEL 617-273-9080 bull FAX 617-273-9084
07161996 1658 6179444082 CASHIMS 3 ASSOCIATES PAGE 03
CASHINSamp Associates Inc
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CLIENT T Ford Company t lP ~ ff2-r
LOCATION Sal era Acraa Suplaquorfund Sj-ta 8L-4 Araa
DATES INCLUDED IN SUMMARY
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55 CAMBRIDGE STREET bull SUITE 201 bull 8URUNGTON MA 01803 bull TEL 617-273-9080 bull FAX 617-273-90W
07151996 18 fO 6179444082 CASHINS S ASSOCIATES PAGE 02
CASHINS amp Associates Inc
WBBKLY HEALTH amp SAFETY FLAK COMPLIANCE SUMMARY REPORT
CLIENT T Ford Compapv
LOCATION i Sal am Acrlaquolaquo Suparfund Sita SL-4 Area
DATES INCLUDED IN SUMMARY i bull pound7 mdash
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SXWMARIZ2D BY FOR CASHINS amp ASSOCIATES INC (
55 CAMBRIDGE STREET SUITE 201 bull SURtlNCTON MA 01803 TEL 617-273-9080 bull FAX 61 7-273-9084
- barcode 14732
- barcodetext SEMS Doc ID 14732
![Page 57: SALEM ACRES SUPERFUND SITE SALEM, MA ...The truck loading pa d consisted of a crushed stone are sea t up along the east sid e o f SL-4 adjacent to the access road A. row of concrete](https://reader036.vdocuments.us/reader036/viewer/2022070114/60729b840fec4e6b4d136a16/html5/thumbnails/57.jpg)
CASHING X ASSOCIATES PAGE
1C n -044408shy07161336 1650 61 344408shy
CASHINSamp Associates Inc
WEEKLY HEALTH amp SAFBTT PLAN COMPLIANCE SUMMARY REPORT
CLIENT ^T Ford Combanv
LOCATION Salam Aerag SL-4
DATES INCLUDED IN SUMMARY
- ^ ^
MS
tct
W
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SUMMARIZED BY FOR CASHINS amp ASSOCIATES INC
55 CAMBRIDGE STREET bull SUITE 201 bull SURUNCTON vu 01803 TEL 61 rori-^oao FAX 61 ~ rj
07161996 1650 6179444082 CASHI MS amp ASSOCIATES PAGE 10
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CA5HIN3 i AH30CIATES INC
55 CAM8RJDCpound STWET bull SUTTE201 eolaquolNCTONMAOJlaquo03 TIL 6t7shy
07161996 1650 6179444082 CASH INS amp ASSOCIATES PAGE 08
CASHINSamp Associates Inc
Intutttitl Myffcnt t InvtmnmmUt Itnl
WEEKLY HEALTH 6 SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Fortjl Cqjapany
LOCATION Salem Acrlaquoa Superfund Site 9L-4 Area
DATES INCLUDED IN SUMMARY
s
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ampspounde
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SUMMARIZED BY FOR CASKINS amp ASSOCIATES INC
55 CAMBRIDGE STREFT SUITE 201 bull BURUNCTON MA oisoa bull TEL 617-273-9030 bull FAX 6i 7-273-9084
77
OSHINSamp Associates Inc
Industrial Hygiene amp Emironmvntal Testing
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Company
LOCATION Salem Acres Superfund Site SL-4 Area
DATES INCLUDED IN SUMMARY J_
pound0
77
cftf r
SUMMARIZED BY FOR CASHINS amp ASSOCIATES INC
5 CAMBRIDGE STREET bull SUITE JO I bull BURLINGTON MA 01 K03 TEL ltjl 7-J7J-9080 bull FAX b I 7-273-9084
CASHINS amp Associates Inc
Industrial Hygifnr amp [nvironmenljl res
SERIOUS HAZARD NOTIFICATION
ISSUED TO REPRESENTING
ISSUED BY REPRESENTING CASHINS S ASSOCIATES INcT DAY DATE ISSUED O04Xmdash 1 bull-bullmdashbull f P^JT
PROJECT NAME_ SITE LOCATION
THE PURPOSE OF THE FOLLOWING STATEMENT IS TO DOCUMENT THE EXISTENCE OF A CONDITION OR CONCERN WHICH CASHINS amp ASSOCIATES INC BELIEVES WARRANTS IMMEDIATE CORRECTIVE ACTION POSSIBLE SOLUTIONS AND OR CORRECTIVE ACTIONS WILL BE INCLUDED IN THIS NOTIFICATION WHEN POSSIBLE THIS NOTIFICATION IS LIMITED TO SITUATIONS THAT REPRESENT EITHER IMMEDIATE DANGER TO LIFE OR HEALTH CONDITIONS OR PREVIOUSLY IDENTIFIED CHRONIC PROBLEMS THAT UNDERMINE OUR ABILITY TO EFFECTIVELY INSURE COMPLIANCE WITH THE REQUIREMENTS OF THE HEALTH AND SAFETY PLAN
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55 CAMBRIDGE STREET bull SUITE 201 bull BURLINGTON MA 01 803 bull TEL 61 7-273-9080 bull FAX fgtl 7-273-9084
CISHINS amp Associates Inc
Industrial Hygirne amp Cmimnmtntal Testing
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Company
LOCATION Salem Acres Superfund Site SL-4 Area
DATES INCLUDED IN SUMMARY T
(5 f0^ degT a
pound btU-pcfa _ J _
- ltpfampo
(J -gt ft
SUMMARIZED BY FOR CASHINS amp ASSOCIATES INC
f a 7 ) ) F A X i gt I 7-273-^)84
87161996 1650 6179444882 CASHINS amp ASSOCIATES
CASHINSamp Associates Inc
WEEKLY HEALTH amp SA7STT PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Coqpanv
LOCATION Sa^am Acras Super fund 5 jte SL-4 Area
DATES INCLUDED IN SUMMARY bull
11 bdquo mdashbull - ampruzpoundtC4 poundLampu ^6zUT
b( I fa We
FOR CASHINS amp ASSOCIATES INC
53 CAMBRIDGE STREET bull SUTE40I bull BURIJSCTON MA 0803 TfL 61 7-273-908O bull FAX fairo-Jshy
07161996 1658 6179444032 CASHINS S ASSOCIATES PAGE 86
CASHINSamp Associates Inc
MtanW HriHtif A
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT ^ mdash
CLIENT T Ford Company
LOCATION Salem Acraa Suoerfund Sita 5L-4
DATES INCLUDED IN SUMMARY bull
6 03 HL fro- TH4-shy
lt Go
i
tOOf
fo
SUMMARIZED BY FOR CASHINS amp ASSOCIATES INC
55 CAMBRIDGE STREET bullSUITE 201 bull BURllNCTON MA 01803 bull TEL 617-273-9080 bull FAX 617-273-9084
07161996 1650 617944408 CASHING 3 ASSOCIATES PAGE 05
CASHINSamp Associates Inc
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WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT t T Ford Coimbanv
LOCATION t Salam Acraa Suoarfund Site SL-4 Arlaquoa
DATES INCLUDED IN SUMMARYj pound mdashiffofrshy f
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55 CAMBRIDGE STREET bull SUITE 201 bull BURLINGTON MA 01803 lt TEL 617-273-9080 bull FAX 617-273-9084
CASHIMS amp ASSOCIATES PAGE 04 07161996 1658 6179444032
OVSHINSamp Associates Inc
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Company T
LOCATION Salem AcrM Suoerfund Stta 8L-4 Araa
DATES INCLUDED IN SUMMARY
(7
ft ^ 0
SUMMARIZED BY pound FOR CASHINS amp ASSOCIATES INC
55 CAMBRIDGE STREET bull SUITE 201 bull BURUNGTON MA 01803 bull TEL 617-273-9080 bull FAX 617-273-9084
07161996 1658 6179444082 CASHIMS 3 ASSOCIATES PAGE 03
CASHINSamp Associates Inc
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CLIENT T Ford Company t lP ~ ff2-r
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DATES INCLUDED IN SUMMARY
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55 CAMBRIDGE STREET bull SUITE 201 bull 8URUNGTON MA 01803 bull TEL 617-273-9080 bull FAX 617-273-90W
07151996 18 fO 6179444082 CASHINS S ASSOCIATES PAGE 02
CASHINS amp Associates Inc
WBBKLY HEALTH amp SAFETY FLAK COMPLIANCE SUMMARY REPORT
CLIENT T Ford Compapv
LOCATION i Sal am Acrlaquolaquo Suparfund Sita SL-4 Area
DATES INCLUDED IN SUMMARY i bull pound7 mdash
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SXWMARIZ2D BY FOR CASHINS amp ASSOCIATES INC (
55 CAMBRIDGE STREET SUITE 201 bull SURtlNCTON MA 01803 TEL 617-273-9080 bull FAX 61 7-273-9084
- barcode 14732
- barcodetext SEMS Doc ID 14732
![Page 58: SALEM ACRES SUPERFUND SITE SALEM, MA ...The truck loading pa d consisted of a crushed stone are sea t up along the east sid e o f SL-4 adjacent to the access road A. row of concrete](https://reader036.vdocuments.us/reader036/viewer/2022070114/60729b840fec4e6b4d136a16/html5/thumbnails/58.jpg)
07161996 1650 6179444082 CASHI MS amp ASSOCIATES PAGE 10
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07161996 1650 6179444082 CASH INS amp ASSOCIATES PAGE 08
CASHINSamp Associates Inc
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WEEKLY HEALTH 6 SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Fortjl Cqjapany
LOCATION Salem Acrlaquoa Superfund Site 9L-4 Area
DATES INCLUDED IN SUMMARY
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55 CAMBRIDGE STREFT SUITE 201 bull BURUNCTON MA oisoa bull TEL 617-273-9030 bull FAX 6i 7-273-9084
77
OSHINSamp Associates Inc
Industrial Hygiene amp Emironmvntal Testing
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Company
LOCATION Salem Acres Superfund Site SL-4 Area
DATES INCLUDED IN SUMMARY J_
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77
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SUMMARIZED BY FOR CASHINS amp ASSOCIATES INC
5 CAMBRIDGE STREET bull SUITE JO I bull BURLINGTON MA 01 K03 TEL ltjl 7-J7J-9080 bull FAX b I 7-273-9084
CASHINS amp Associates Inc
Industrial Hygifnr amp [nvironmenljl res
SERIOUS HAZARD NOTIFICATION
ISSUED TO REPRESENTING
ISSUED BY REPRESENTING CASHINS S ASSOCIATES INcT DAY DATE ISSUED O04Xmdash 1 bull-bullmdashbull f P^JT
PROJECT NAME_ SITE LOCATION
THE PURPOSE OF THE FOLLOWING STATEMENT IS TO DOCUMENT THE EXISTENCE OF A CONDITION OR CONCERN WHICH CASHINS amp ASSOCIATES INC BELIEVES WARRANTS IMMEDIATE CORRECTIVE ACTION POSSIBLE SOLUTIONS AND OR CORRECTIVE ACTIONS WILL BE INCLUDED IN THIS NOTIFICATION WHEN POSSIBLE THIS NOTIFICATION IS LIMITED TO SITUATIONS THAT REPRESENT EITHER IMMEDIATE DANGER TO LIFE OR HEALTH CONDITIONS OR PREVIOUSLY IDENTIFIED CHRONIC PROBLEMS THAT UNDERMINE OUR ABILITY TO EFFECTIVELY INSURE COMPLIANCE WITH THE REQUIREMENTS OF THE HEALTH AND SAFETY PLAN
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55 CAMBRIDGE STREET bull SUITE 201 bull BURLINGTON MA 01 803 bull TEL 61 7-273-9080 bull FAX fgtl 7-273-9084
CISHINS amp Associates Inc
Industrial Hygirne amp Cmimnmtntal Testing
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Company
LOCATION Salem Acres Superfund Site SL-4 Area
DATES INCLUDED IN SUMMARY T
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SUMMARIZED BY FOR CASHINS amp ASSOCIATES INC
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87161996 1650 6179444882 CASHINS amp ASSOCIATES
CASHINSamp Associates Inc
WEEKLY HEALTH amp SA7STT PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Coqpanv
LOCATION Sa^am Acras Super fund 5 jte SL-4 Area
DATES INCLUDED IN SUMMARY bull
11 bdquo mdashbull - ampruzpoundtC4 poundLampu ^6zUT
b( I fa We
FOR CASHINS amp ASSOCIATES INC
53 CAMBRIDGE STREET bull SUTE40I bull BURIJSCTON MA 0803 TfL 61 7-273-908O bull FAX fairo-Jshy
07161996 1658 6179444032 CASHINS S ASSOCIATES PAGE 86
CASHINSamp Associates Inc
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WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT ^ mdash
CLIENT T Ford Company
LOCATION Salem Acraa Suoerfund Sita 5L-4
DATES INCLUDED IN SUMMARY bull
6 03 HL fro- TH4-shy
lt Go
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SUMMARIZED BY FOR CASHINS amp ASSOCIATES INC
55 CAMBRIDGE STREET bullSUITE 201 bull BURllNCTON MA 01803 bull TEL 617-273-9080 bull FAX 617-273-9084
07161996 1650 617944408 CASHING 3 ASSOCIATES PAGE 05
CASHINSamp Associates Inc
fmimnntattl few
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT t T Ford Coimbanv
LOCATION t Salam Acraa Suoarfund Site SL-4 Arlaquoa
DATES INCLUDED IN SUMMARYj pound mdashiffofrshy f
K (J
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SUMMARIZ2D BY _ ampampS FOR CASHINS amp ASSOCIATES INC
55 CAMBRIDGE STREET bull SUITE 201 bull BURLINGTON MA 01803 lt TEL 617-273-9080 bull FAX 617-273-9084
CASHIMS amp ASSOCIATES PAGE 04 07161996 1658 6179444032
OVSHINSamp Associates Inc
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Company T
LOCATION Salem AcrM Suoerfund Stta 8L-4 Araa
DATES INCLUDED IN SUMMARY
(7
ft ^ 0
SUMMARIZED BY pound FOR CASHINS amp ASSOCIATES INC
55 CAMBRIDGE STREET bull SUITE 201 bull BURUNGTON MA 01803 bull TEL 617-273-9080 bull FAX 617-273-9084
07161996 1658 6179444082 CASHIMS 3 ASSOCIATES PAGE 03
CASHINSamp Associates Inc
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CLIENT T Ford Company t lP ~ ff2-r
LOCATION Sal era Acraa Suplaquorfund Sj-ta 8L-4 Araa
DATES INCLUDED IN SUMMARY
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55 CAMBRIDGE STREET bull SUITE 201 bull 8URUNGTON MA 01803 bull TEL 617-273-9080 bull FAX 617-273-90W
07151996 18 fO 6179444082 CASHINS S ASSOCIATES PAGE 02
CASHINS amp Associates Inc
WBBKLY HEALTH amp SAFETY FLAK COMPLIANCE SUMMARY REPORT
CLIENT T Ford Compapv
LOCATION i Sal am Acrlaquolaquo Suparfund Sita SL-4 Area
DATES INCLUDED IN SUMMARY i bull pound7 mdash
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SXWMARIZ2D BY FOR CASHINS amp ASSOCIATES INC (
55 CAMBRIDGE STREET SUITE 201 bull SURtlNCTON MA 01803 TEL 617-273-9080 bull FAX 61 7-273-9084
- barcode 14732
- barcodetext SEMS Doc ID 14732
![Page 59: SALEM ACRES SUPERFUND SITE SALEM, MA ...The truck loading pa d consisted of a crushed stone are sea t up along the east sid e o f SL-4 adjacent to the access road A. row of concrete](https://reader036.vdocuments.us/reader036/viewer/2022070114/60729b840fec4e6b4d136a16/html5/thumbnails/59.jpg)
07161996 1650 6179444082 CASH INS amp ASSOCIATES PAGE 08
CASHINSamp Associates Inc
Intutttitl Myffcnt t InvtmnmmUt Itnl
WEEKLY HEALTH 6 SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Fortjl Cqjapany
LOCATION Salem Acrlaquoa Superfund Site 9L-4 Area
DATES INCLUDED IN SUMMARY
s
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ampspounde
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SUMMARIZED BY FOR CASKINS amp ASSOCIATES INC
55 CAMBRIDGE STREFT SUITE 201 bull BURUNCTON MA oisoa bull TEL 617-273-9030 bull FAX 6i 7-273-9084
77
OSHINSamp Associates Inc
Industrial Hygiene amp Emironmvntal Testing
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Company
LOCATION Salem Acres Superfund Site SL-4 Area
DATES INCLUDED IN SUMMARY J_
pound0
77
cftf r
SUMMARIZED BY FOR CASHINS amp ASSOCIATES INC
5 CAMBRIDGE STREET bull SUITE JO I bull BURLINGTON MA 01 K03 TEL ltjl 7-J7J-9080 bull FAX b I 7-273-9084
CASHINS amp Associates Inc
Industrial Hygifnr amp [nvironmenljl res
SERIOUS HAZARD NOTIFICATION
ISSUED TO REPRESENTING
ISSUED BY REPRESENTING CASHINS S ASSOCIATES INcT DAY DATE ISSUED O04Xmdash 1 bull-bullmdashbull f P^JT
PROJECT NAME_ SITE LOCATION
THE PURPOSE OF THE FOLLOWING STATEMENT IS TO DOCUMENT THE EXISTENCE OF A CONDITION OR CONCERN WHICH CASHINS amp ASSOCIATES INC BELIEVES WARRANTS IMMEDIATE CORRECTIVE ACTION POSSIBLE SOLUTIONS AND OR CORRECTIVE ACTIONS WILL BE INCLUDED IN THIS NOTIFICATION WHEN POSSIBLE THIS NOTIFICATION IS LIMITED TO SITUATIONS THAT REPRESENT EITHER IMMEDIATE DANGER TO LIFE OR HEALTH CONDITIONS OR PREVIOUSLY IDENTIFIED CHRONIC PROBLEMS THAT UNDERMINE OUR ABILITY TO EFFECTIVELY INSURE COMPLIANCE WITH THE REQUIREMENTS OF THE HEALTH AND SAFETY PLAN
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55 CAMBRIDGE STREET bull SUITE 201 bull BURLINGTON MA 01 803 bull TEL 61 7-273-9080 bull FAX fgtl 7-273-9084
CISHINS amp Associates Inc
Industrial Hygirne amp Cmimnmtntal Testing
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Company
LOCATION Salem Acres Superfund Site SL-4 Area
DATES INCLUDED IN SUMMARY T
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87161996 1650 6179444882 CASHINS amp ASSOCIATES
CASHINSamp Associates Inc
WEEKLY HEALTH amp SA7STT PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Coqpanv
LOCATION Sa^am Acras Super fund 5 jte SL-4 Area
DATES INCLUDED IN SUMMARY bull
11 bdquo mdashbull - ampruzpoundtC4 poundLampu ^6zUT
b( I fa We
FOR CASHINS amp ASSOCIATES INC
53 CAMBRIDGE STREET bull SUTE40I bull BURIJSCTON MA 0803 TfL 61 7-273-908O bull FAX fairo-Jshy
07161996 1658 6179444032 CASHINS S ASSOCIATES PAGE 86
CASHINSamp Associates Inc
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WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT ^ mdash
CLIENT T Ford Company
LOCATION Salem Acraa Suoerfund Sita 5L-4
DATES INCLUDED IN SUMMARY bull
6 03 HL fro- TH4-shy
lt Go
i
tOOf
fo
SUMMARIZED BY FOR CASHINS amp ASSOCIATES INC
55 CAMBRIDGE STREET bullSUITE 201 bull BURllNCTON MA 01803 bull TEL 617-273-9080 bull FAX 617-273-9084
07161996 1650 617944408 CASHING 3 ASSOCIATES PAGE 05
CASHINSamp Associates Inc
fmimnntattl few
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT t T Ford Coimbanv
LOCATION t Salam Acraa Suoarfund Site SL-4 Arlaquoa
DATES INCLUDED IN SUMMARYj pound mdashiffofrshy f
K (J
-ficuts O
SUMMARIZ2D BY _ ampampS FOR CASHINS amp ASSOCIATES INC
55 CAMBRIDGE STREET bull SUITE 201 bull BURLINGTON MA 01803 lt TEL 617-273-9080 bull FAX 617-273-9084
CASHIMS amp ASSOCIATES PAGE 04 07161996 1658 6179444032
OVSHINSamp Associates Inc
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Company T
LOCATION Salem AcrM Suoerfund Stta 8L-4 Araa
DATES INCLUDED IN SUMMARY
(7
ft ^ 0
SUMMARIZED BY pound FOR CASHINS amp ASSOCIATES INC
55 CAMBRIDGE STREET bull SUITE 201 bull BURUNGTON MA 01803 bull TEL 617-273-9080 bull FAX 617-273-9084
07161996 1658 6179444082 CASHIMS 3 ASSOCIATES PAGE 03
CASHINSamp Associates Inc
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WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT ^
CLIENT T Ford Company t lP ~ ff2-r
LOCATION Sal era Acraa Suplaquorfund Sj-ta 8L-4 Araa
DATES INCLUDED IN SUMMARY
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55 CAMBRIDGE STREET bull SUITE 201 bull 8URUNGTON MA 01803 bull TEL 617-273-9080 bull FAX 617-273-90W
07151996 18 fO 6179444082 CASHINS S ASSOCIATES PAGE 02
CASHINS amp Associates Inc
WBBKLY HEALTH amp SAFETY FLAK COMPLIANCE SUMMARY REPORT
CLIENT T Ford Compapv
LOCATION i Sal am Acrlaquolaquo Suparfund Sita SL-4 Area
DATES INCLUDED IN SUMMARY i bull pound7 mdash
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SXWMARIZ2D BY FOR CASHINS amp ASSOCIATES INC (
55 CAMBRIDGE STREET SUITE 201 bull SURtlNCTON MA 01803 TEL 617-273-9080 bull FAX 61 7-273-9084
- barcode 14732
- barcodetext SEMS Doc ID 14732
![Page 60: SALEM ACRES SUPERFUND SITE SALEM, MA ...The truck loading pa d consisted of a crushed stone are sea t up along the east sid e o f SL-4 adjacent to the access road A. row of concrete](https://reader036.vdocuments.us/reader036/viewer/2022070114/60729b840fec4e6b4d136a16/html5/thumbnails/60.jpg)
77
OSHINSamp Associates Inc
Industrial Hygiene amp Emironmvntal Testing
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Company
LOCATION Salem Acres Superfund Site SL-4 Area
DATES INCLUDED IN SUMMARY J_
pound0
77
cftf r
SUMMARIZED BY FOR CASHINS amp ASSOCIATES INC
5 CAMBRIDGE STREET bull SUITE JO I bull BURLINGTON MA 01 K03 TEL ltjl 7-J7J-9080 bull FAX b I 7-273-9084
CASHINS amp Associates Inc
Industrial Hygifnr amp [nvironmenljl res
SERIOUS HAZARD NOTIFICATION
ISSUED TO REPRESENTING
ISSUED BY REPRESENTING CASHINS S ASSOCIATES INcT DAY DATE ISSUED O04Xmdash 1 bull-bullmdashbull f P^JT
PROJECT NAME_ SITE LOCATION
THE PURPOSE OF THE FOLLOWING STATEMENT IS TO DOCUMENT THE EXISTENCE OF A CONDITION OR CONCERN WHICH CASHINS amp ASSOCIATES INC BELIEVES WARRANTS IMMEDIATE CORRECTIVE ACTION POSSIBLE SOLUTIONS AND OR CORRECTIVE ACTIONS WILL BE INCLUDED IN THIS NOTIFICATION WHEN POSSIBLE THIS NOTIFICATION IS LIMITED TO SITUATIONS THAT REPRESENT EITHER IMMEDIATE DANGER TO LIFE OR HEALTH CONDITIONS OR PREVIOUSLY IDENTIFIED CHRONIC PROBLEMS THAT UNDERMINE OUR ABILITY TO EFFECTIVELY INSURE COMPLIANCE WITH THE REQUIREMENTS OF THE HEALTH AND SAFETY PLAN
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ACKNOWLEDGEMENT OF ISSUANCE OF NOTIFICATION - NAMECOMPANY ^gt j^f^u^^ CASHINS amp ASSOCINC DATE0 IS
55 CAMBRIDGE STREET bull SUITE 201 bull BURLINGTON MA 01 803 bull TEL 61 7-273-9080 bull FAX fgtl 7-273-9084
CISHINS amp Associates Inc
Industrial Hygirne amp Cmimnmtntal Testing
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Company
LOCATION Salem Acres Superfund Site SL-4 Area
DATES INCLUDED IN SUMMARY T
(5 f0^ degT a
pound btU-pcfa _ J _
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(J -gt ft
SUMMARIZED BY FOR CASHINS amp ASSOCIATES INC
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87161996 1650 6179444882 CASHINS amp ASSOCIATES
CASHINSamp Associates Inc
WEEKLY HEALTH amp SA7STT PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Coqpanv
LOCATION Sa^am Acras Super fund 5 jte SL-4 Area
DATES INCLUDED IN SUMMARY bull
11 bdquo mdashbull - ampruzpoundtC4 poundLampu ^6zUT
b( I fa We
FOR CASHINS amp ASSOCIATES INC
53 CAMBRIDGE STREET bull SUTE40I bull BURIJSCTON MA 0803 TfL 61 7-273-908O bull FAX fairo-Jshy
07161996 1658 6179444032 CASHINS S ASSOCIATES PAGE 86
CASHINSamp Associates Inc
MtanW HriHtif A
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT ^ mdash
CLIENT T Ford Company
LOCATION Salem Acraa Suoerfund Sita 5L-4
DATES INCLUDED IN SUMMARY bull
6 03 HL fro- TH4-shy
lt Go
i
tOOf
fo
SUMMARIZED BY FOR CASHINS amp ASSOCIATES INC
55 CAMBRIDGE STREET bullSUITE 201 bull BURllNCTON MA 01803 bull TEL 617-273-9080 bull FAX 617-273-9084
07161996 1650 617944408 CASHING 3 ASSOCIATES PAGE 05
CASHINSamp Associates Inc
fmimnntattl few
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT t T Ford Coimbanv
LOCATION t Salam Acraa Suoarfund Site SL-4 Arlaquoa
DATES INCLUDED IN SUMMARYj pound mdashiffofrshy f
K (J
-ficuts O
SUMMARIZ2D BY _ ampampS FOR CASHINS amp ASSOCIATES INC
55 CAMBRIDGE STREET bull SUITE 201 bull BURLINGTON MA 01803 lt TEL 617-273-9080 bull FAX 617-273-9084
CASHIMS amp ASSOCIATES PAGE 04 07161996 1658 6179444032
OVSHINSamp Associates Inc
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Company T
LOCATION Salem AcrM Suoerfund Stta 8L-4 Araa
DATES INCLUDED IN SUMMARY
(7
ft ^ 0
SUMMARIZED BY pound FOR CASHINS amp ASSOCIATES INC
55 CAMBRIDGE STREET bull SUITE 201 bull BURUNGTON MA 01803 bull TEL 617-273-9080 bull FAX 617-273-9084
07161996 1658 6179444082 CASHIMS 3 ASSOCIATES PAGE 03
CASHINSamp Associates Inc
ndurtrW Hrtnm t
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT ^
CLIENT T Ford Company t lP ~ ff2-r
LOCATION Sal era Acraa Suplaquorfund Sj-ta 8L-4 Araa
DATES INCLUDED IN SUMMARY
if
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55 CAMBRIDGE STREET bull SUITE 201 bull 8URUNGTON MA 01803 bull TEL 617-273-9080 bull FAX 617-273-90W
07151996 18 fO 6179444082 CASHINS S ASSOCIATES PAGE 02
CASHINS amp Associates Inc
WBBKLY HEALTH amp SAFETY FLAK COMPLIANCE SUMMARY REPORT
CLIENT T Ford Compapv
LOCATION i Sal am Acrlaquolaquo Suparfund Sita SL-4 Area
DATES INCLUDED IN SUMMARY i bull pound7 mdash
A 0-3 - A)
SXWMARIZ2D BY FOR CASHINS amp ASSOCIATES INC (
55 CAMBRIDGE STREET SUITE 201 bull SURtlNCTON MA 01803 TEL 617-273-9080 bull FAX 61 7-273-9084
- barcode 14732
- barcodetext SEMS Doc ID 14732
![Page 61: SALEM ACRES SUPERFUND SITE SALEM, MA ...The truck loading pa d consisted of a crushed stone are sea t up along the east sid e o f SL-4 adjacent to the access road A. row of concrete](https://reader036.vdocuments.us/reader036/viewer/2022070114/60729b840fec4e6b4d136a16/html5/thumbnails/61.jpg)
CASHINS amp Associates Inc
Industrial Hygifnr amp [nvironmenljl res
SERIOUS HAZARD NOTIFICATION
ISSUED TO REPRESENTING
ISSUED BY REPRESENTING CASHINS S ASSOCIATES INcT DAY DATE ISSUED O04Xmdash 1 bull-bullmdashbull f P^JT
PROJECT NAME_ SITE LOCATION
THE PURPOSE OF THE FOLLOWING STATEMENT IS TO DOCUMENT THE EXISTENCE OF A CONDITION OR CONCERN WHICH CASHINS amp ASSOCIATES INC BELIEVES WARRANTS IMMEDIATE CORRECTIVE ACTION POSSIBLE SOLUTIONS AND OR CORRECTIVE ACTIONS WILL BE INCLUDED IN THIS NOTIFICATION WHEN POSSIBLE THIS NOTIFICATION IS LIMITED TO SITUATIONS THAT REPRESENT EITHER IMMEDIATE DANGER TO LIFE OR HEALTH CONDITIONS OR PREVIOUSLY IDENTIFIED CHRONIC PROBLEMS THAT UNDERMINE OUR ABILITY TO EFFECTIVELY INSURE COMPLIANCE WITH THE REQUIREMENTS OF THE HEALTH AND SAFETY PLAN
0
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ACKNOWLEDGEMENT OF RECEIPT OF NOTIFICATION NAMECOMPANY DATE
ACKNOWLEDGEMENT OF ISSUANCE OF NOTIFICATION - NAMECOMPANY ^gt j^f^u^^ CASHINS amp ASSOCINC DATE0 IS
55 CAMBRIDGE STREET bull SUITE 201 bull BURLINGTON MA 01 803 bull TEL 61 7-273-9080 bull FAX fgtl 7-273-9084
CISHINS amp Associates Inc
Industrial Hygirne amp Cmimnmtntal Testing
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Company
LOCATION Salem Acres Superfund Site SL-4 Area
DATES INCLUDED IN SUMMARY T
(5 f0^ degT a
pound btU-pcfa _ J _
- ltpfampo
(J -gt ft
SUMMARIZED BY FOR CASHINS amp ASSOCIATES INC
f a 7 ) ) F A X i gt I 7-273-^)84
87161996 1650 6179444882 CASHINS amp ASSOCIATES
CASHINSamp Associates Inc
WEEKLY HEALTH amp SA7STT PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Coqpanv
LOCATION Sa^am Acras Super fund 5 jte SL-4 Area
DATES INCLUDED IN SUMMARY bull
11 bdquo mdashbull - ampruzpoundtC4 poundLampu ^6zUT
b( I fa We
FOR CASHINS amp ASSOCIATES INC
53 CAMBRIDGE STREET bull SUTE40I bull BURIJSCTON MA 0803 TfL 61 7-273-908O bull FAX fairo-Jshy
07161996 1658 6179444032 CASHINS S ASSOCIATES PAGE 86
CASHINSamp Associates Inc
MtanW HriHtif A
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT ^ mdash
CLIENT T Ford Company
LOCATION Salem Acraa Suoerfund Sita 5L-4
DATES INCLUDED IN SUMMARY bull
6 03 HL fro- TH4-shy
lt Go
i
tOOf
fo
SUMMARIZED BY FOR CASHINS amp ASSOCIATES INC
55 CAMBRIDGE STREET bullSUITE 201 bull BURllNCTON MA 01803 bull TEL 617-273-9080 bull FAX 617-273-9084
07161996 1650 617944408 CASHING 3 ASSOCIATES PAGE 05
CASHINSamp Associates Inc
fmimnntattl few
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT t T Ford Coimbanv
LOCATION t Salam Acraa Suoarfund Site SL-4 Arlaquoa
DATES INCLUDED IN SUMMARYj pound mdashiffofrshy f
K (J
-ficuts O
SUMMARIZ2D BY _ ampampS FOR CASHINS amp ASSOCIATES INC
55 CAMBRIDGE STREET bull SUITE 201 bull BURLINGTON MA 01803 lt TEL 617-273-9080 bull FAX 617-273-9084
CASHIMS amp ASSOCIATES PAGE 04 07161996 1658 6179444032
OVSHINSamp Associates Inc
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Company T
LOCATION Salem AcrM Suoerfund Stta 8L-4 Araa
DATES INCLUDED IN SUMMARY
(7
ft ^ 0
SUMMARIZED BY pound FOR CASHINS amp ASSOCIATES INC
55 CAMBRIDGE STREET bull SUITE 201 bull BURUNGTON MA 01803 bull TEL 617-273-9080 bull FAX 617-273-9084
07161996 1658 6179444082 CASHIMS 3 ASSOCIATES PAGE 03
CASHINSamp Associates Inc
ndurtrW Hrtnm t
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT ^
CLIENT T Ford Company t lP ~ ff2-r
LOCATION Sal era Acraa Suplaquorfund Sj-ta 8L-4 Araa
DATES INCLUDED IN SUMMARY
if
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SUMMARIZED BY FOR CASMINS amp ASSOCIATES INC
55 CAMBRIDGE STREET bull SUITE 201 bull 8URUNGTON MA 01803 bull TEL 617-273-9080 bull FAX 617-273-90W
07151996 18 fO 6179444082 CASHINS S ASSOCIATES PAGE 02
CASHINS amp Associates Inc
WBBKLY HEALTH amp SAFETY FLAK COMPLIANCE SUMMARY REPORT
CLIENT T Ford Compapv
LOCATION i Sal am Acrlaquolaquo Suparfund Sita SL-4 Area
DATES INCLUDED IN SUMMARY i bull pound7 mdash
A 0-3 - A)
SXWMARIZ2D BY FOR CASHINS amp ASSOCIATES INC (
55 CAMBRIDGE STREET SUITE 201 bull SURtlNCTON MA 01803 TEL 617-273-9080 bull FAX 61 7-273-9084
- barcode 14732
- barcodetext SEMS Doc ID 14732
![Page 62: SALEM ACRES SUPERFUND SITE SALEM, MA ...The truck loading pa d consisted of a crushed stone are sea t up along the east sid e o f SL-4 adjacent to the access road A. row of concrete](https://reader036.vdocuments.us/reader036/viewer/2022070114/60729b840fec4e6b4d136a16/html5/thumbnails/62.jpg)
CISHINS amp Associates Inc
Industrial Hygirne amp Cmimnmtntal Testing
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Company
LOCATION Salem Acres Superfund Site SL-4 Area
DATES INCLUDED IN SUMMARY T
(5 f0^ degT a
pound btU-pcfa _ J _
- ltpfampo
(J -gt ft
SUMMARIZED BY FOR CASHINS amp ASSOCIATES INC
f a 7 ) ) F A X i gt I 7-273-^)84
87161996 1650 6179444882 CASHINS amp ASSOCIATES
CASHINSamp Associates Inc
WEEKLY HEALTH amp SA7STT PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Coqpanv
LOCATION Sa^am Acras Super fund 5 jte SL-4 Area
DATES INCLUDED IN SUMMARY bull
11 bdquo mdashbull - ampruzpoundtC4 poundLampu ^6zUT
b( I fa We
FOR CASHINS amp ASSOCIATES INC
53 CAMBRIDGE STREET bull SUTE40I bull BURIJSCTON MA 0803 TfL 61 7-273-908O bull FAX fairo-Jshy
07161996 1658 6179444032 CASHINS S ASSOCIATES PAGE 86
CASHINSamp Associates Inc
MtanW HriHtif A
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT ^ mdash
CLIENT T Ford Company
LOCATION Salem Acraa Suoerfund Sita 5L-4
DATES INCLUDED IN SUMMARY bull
6 03 HL fro- TH4-shy
lt Go
i
tOOf
fo
SUMMARIZED BY FOR CASHINS amp ASSOCIATES INC
55 CAMBRIDGE STREET bullSUITE 201 bull BURllNCTON MA 01803 bull TEL 617-273-9080 bull FAX 617-273-9084
07161996 1650 617944408 CASHING 3 ASSOCIATES PAGE 05
CASHINSamp Associates Inc
fmimnntattl few
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT t T Ford Coimbanv
LOCATION t Salam Acraa Suoarfund Site SL-4 Arlaquoa
DATES INCLUDED IN SUMMARYj pound mdashiffofrshy f
K (J
-ficuts O
SUMMARIZ2D BY _ ampampS FOR CASHINS amp ASSOCIATES INC
55 CAMBRIDGE STREET bull SUITE 201 bull BURLINGTON MA 01803 lt TEL 617-273-9080 bull FAX 617-273-9084
CASHIMS amp ASSOCIATES PAGE 04 07161996 1658 6179444032
OVSHINSamp Associates Inc
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Company T
LOCATION Salem AcrM Suoerfund Stta 8L-4 Araa
DATES INCLUDED IN SUMMARY
(7
ft ^ 0
SUMMARIZED BY pound FOR CASHINS amp ASSOCIATES INC
55 CAMBRIDGE STREET bull SUITE 201 bull BURUNGTON MA 01803 bull TEL 617-273-9080 bull FAX 617-273-9084
07161996 1658 6179444082 CASHIMS 3 ASSOCIATES PAGE 03
CASHINSamp Associates Inc
ndurtrW Hrtnm t
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT ^
CLIENT T Ford Company t lP ~ ff2-r
LOCATION Sal era Acraa Suplaquorfund Sj-ta 8L-4 Araa
DATES INCLUDED IN SUMMARY
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55 CAMBRIDGE STREET bull SUITE 201 bull 8URUNGTON MA 01803 bull TEL 617-273-9080 bull FAX 617-273-90W
07151996 18 fO 6179444082 CASHINS S ASSOCIATES PAGE 02
CASHINS amp Associates Inc
WBBKLY HEALTH amp SAFETY FLAK COMPLIANCE SUMMARY REPORT
CLIENT T Ford Compapv
LOCATION i Sal am Acrlaquolaquo Suparfund Sita SL-4 Area
DATES INCLUDED IN SUMMARY i bull pound7 mdash
A 0-3 - A)
SXWMARIZ2D BY FOR CASHINS amp ASSOCIATES INC (
55 CAMBRIDGE STREET SUITE 201 bull SURtlNCTON MA 01803 TEL 617-273-9080 bull FAX 61 7-273-9084
- barcode 14732
- barcodetext SEMS Doc ID 14732
![Page 63: SALEM ACRES SUPERFUND SITE SALEM, MA ...The truck loading pa d consisted of a crushed stone are sea t up along the east sid e o f SL-4 adjacent to the access road A. row of concrete](https://reader036.vdocuments.us/reader036/viewer/2022070114/60729b840fec4e6b4d136a16/html5/thumbnails/63.jpg)
87161996 1650 6179444882 CASHINS amp ASSOCIATES
CASHINSamp Associates Inc
WEEKLY HEALTH amp SA7STT PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Coqpanv
LOCATION Sa^am Acras Super fund 5 jte SL-4 Area
DATES INCLUDED IN SUMMARY bull
11 bdquo mdashbull - ampruzpoundtC4 poundLampu ^6zUT
b( I fa We
FOR CASHINS amp ASSOCIATES INC
53 CAMBRIDGE STREET bull SUTE40I bull BURIJSCTON MA 0803 TfL 61 7-273-908O bull FAX fairo-Jshy
07161996 1658 6179444032 CASHINS S ASSOCIATES PAGE 86
CASHINSamp Associates Inc
MtanW HriHtif A
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT ^ mdash
CLIENT T Ford Company
LOCATION Salem Acraa Suoerfund Sita 5L-4
DATES INCLUDED IN SUMMARY bull
6 03 HL fro- TH4-shy
lt Go
i
tOOf
fo
SUMMARIZED BY FOR CASHINS amp ASSOCIATES INC
55 CAMBRIDGE STREET bullSUITE 201 bull BURllNCTON MA 01803 bull TEL 617-273-9080 bull FAX 617-273-9084
07161996 1650 617944408 CASHING 3 ASSOCIATES PAGE 05
CASHINSamp Associates Inc
fmimnntattl few
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT t T Ford Coimbanv
LOCATION t Salam Acraa Suoarfund Site SL-4 Arlaquoa
DATES INCLUDED IN SUMMARYj pound mdashiffofrshy f
K (J
-ficuts O
SUMMARIZ2D BY _ ampampS FOR CASHINS amp ASSOCIATES INC
55 CAMBRIDGE STREET bull SUITE 201 bull BURLINGTON MA 01803 lt TEL 617-273-9080 bull FAX 617-273-9084
CASHIMS amp ASSOCIATES PAGE 04 07161996 1658 6179444032
OVSHINSamp Associates Inc
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Company T
LOCATION Salem AcrM Suoerfund Stta 8L-4 Araa
DATES INCLUDED IN SUMMARY
(7
ft ^ 0
SUMMARIZED BY pound FOR CASHINS amp ASSOCIATES INC
55 CAMBRIDGE STREET bull SUITE 201 bull BURUNGTON MA 01803 bull TEL 617-273-9080 bull FAX 617-273-9084
07161996 1658 6179444082 CASHIMS 3 ASSOCIATES PAGE 03
CASHINSamp Associates Inc
ndurtrW Hrtnm t
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT ^
CLIENT T Ford Company t lP ~ ff2-r
LOCATION Sal era Acraa Suplaquorfund Sj-ta 8L-4 Araa
DATES INCLUDED IN SUMMARY
if
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SUMMARIZED BY FOR CASMINS amp ASSOCIATES INC
55 CAMBRIDGE STREET bull SUITE 201 bull 8URUNGTON MA 01803 bull TEL 617-273-9080 bull FAX 617-273-90W
07151996 18 fO 6179444082 CASHINS S ASSOCIATES PAGE 02
CASHINS amp Associates Inc
WBBKLY HEALTH amp SAFETY FLAK COMPLIANCE SUMMARY REPORT
CLIENT T Ford Compapv
LOCATION i Sal am Acrlaquolaquo Suparfund Sita SL-4 Area
DATES INCLUDED IN SUMMARY i bull pound7 mdash
A 0-3 - A)
SXWMARIZ2D BY FOR CASHINS amp ASSOCIATES INC (
55 CAMBRIDGE STREET SUITE 201 bull SURtlNCTON MA 01803 TEL 617-273-9080 bull FAX 61 7-273-9084
- barcode 14732
- barcodetext SEMS Doc ID 14732
![Page 64: SALEM ACRES SUPERFUND SITE SALEM, MA ...The truck loading pa d consisted of a crushed stone are sea t up along the east sid e o f SL-4 adjacent to the access road A. row of concrete](https://reader036.vdocuments.us/reader036/viewer/2022070114/60729b840fec4e6b4d136a16/html5/thumbnails/64.jpg)
07161996 1658 6179444032 CASHINS S ASSOCIATES PAGE 86
CASHINSamp Associates Inc
MtanW HriHtif A
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT ^ mdash
CLIENT T Ford Company
LOCATION Salem Acraa Suoerfund Sita 5L-4
DATES INCLUDED IN SUMMARY bull
6 03 HL fro- TH4-shy
lt Go
i
tOOf
fo
SUMMARIZED BY FOR CASHINS amp ASSOCIATES INC
55 CAMBRIDGE STREET bullSUITE 201 bull BURllNCTON MA 01803 bull TEL 617-273-9080 bull FAX 617-273-9084
07161996 1650 617944408 CASHING 3 ASSOCIATES PAGE 05
CASHINSamp Associates Inc
fmimnntattl few
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT t T Ford Coimbanv
LOCATION t Salam Acraa Suoarfund Site SL-4 Arlaquoa
DATES INCLUDED IN SUMMARYj pound mdashiffofrshy f
K (J
-ficuts O
SUMMARIZ2D BY _ ampampS FOR CASHINS amp ASSOCIATES INC
55 CAMBRIDGE STREET bull SUITE 201 bull BURLINGTON MA 01803 lt TEL 617-273-9080 bull FAX 617-273-9084
CASHIMS amp ASSOCIATES PAGE 04 07161996 1658 6179444032
OVSHINSamp Associates Inc
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Company T
LOCATION Salem AcrM Suoerfund Stta 8L-4 Araa
DATES INCLUDED IN SUMMARY
(7
ft ^ 0
SUMMARIZED BY pound FOR CASHINS amp ASSOCIATES INC
55 CAMBRIDGE STREET bull SUITE 201 bull BURUNGTON MA 01803 bull TEL 617-273-9080 bull FAX 617-273-9084
07161996 1658 6179444082 CASHIMS 3 ASSOCIATES PAGE 03
CASHINSamp Associates Inc
ndurtrW Hrtnm t
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT ^
CLIENT T Ford Company t lP ~ ff2-r
LOCATION Sal era Acraa Suplaquorfund Sj-ta 8L-4 Araa
DATES INCLUDED IN SUMMARY
if
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SUMMARIZED BY FOR CASMINS amp ASSOCIATES INC
55 CAMBRIDGE STREET bull SUITE 201 bull 8URUNGTON MA 01803 bull TEL 617-273-9080 bull FAX 617-273-90W
07151996 18 fO 6179444082 CASHINS S ASSOCIATES PAGE 02
CASHINS amp Associates Inc
WBBKLY HEALTH amp SAFETY FLAK COMPLIANCE SUMMARY REPORT
CLIENT T Ford Compapv
LOCATION i Sal am Acrlaquolaquo Suparfund Sita SL-4 Area
DATES INCLUDED IN SUMMARY i bull pound7 mdash
A 0-3 - A)
SXWMARIZ2D BY FOR CASHINS amp ASSOCIATES INC (
55 CAMBRIDGE STREET SUITE 201 bull SURtlNCTON MA 01803 TEL 617-273-9080 bull FAX 61 7-273-9084
- barcode 14732
- barcodetext SEMS Doc ID 14732
![Page 65: SALEM ACRES SUPERFUND SITE SALEM, MA ...The truck loading pa d consisted of a crushed stone are sea t up along the east sid e o f SL-4 adjacent to the access road A. row of concrete](https://reader036.vdocuments.us/reader036/viewer/2022070114/60729b840fec4e6b4d136a16/html5/thumbnails/65.jpg)
07161996 1650 617944408 CASHING 3 ASSOCIATES PAGE 05
CASHINSamp Associates Inc
fmimnntattl few
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT t T Ford Coimbanv
LOCATION t Salam Acraa Suoarfund Site SL-4 Arlaquoa
DATES INCLUDED IN SUMMARYj pound mdashiffofrshy f
K (J
-ficuts O
SUMMARIZ2D BY _ ampampS FOR CASHINS amp ASSOCIATES INC
55 CAMBRIDGE STREET bull SUITE 201 bull BURLINGTON MA 01803 lt TEL 617-273-9080 bull FAX 617-273-9084
CASHIMS amp ASSOCIATES PAGE 04 07161996 1658 6179444032
OVSHINSamp Associates Inc
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Company T
LOCATION Salem AcrM Suoerfund Stta 8L-4 Araa
DATES INCLUDED IN SUMMARY
(7
ft ^ 0
SUMMARIZED BY pound FOR CASHINS amp ASSOCIATES INC
55 CAMBRIDGE STREET bull SUITE 201 bull BURUNGTON MA 01803 bull TEL 617-273-9080 bull FAX 617-273-9084
07161996 1658 6179444082 CASHIMS 3 ASSOCIATES PAGE 03
CASHINSamp Associates Inc
ndurtrW Hrtnm t
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT ^
CLIENT T Ford Company t lP ~ ff2-r
LOCATION Sal era Acraa Suplaquorfund Sj-ta 8L-4 Araa
DATES INCLUDED IN SUMMARY
if
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SUMMARIZED BY FOR CASMINS amp ASSOCIATES INC
55 CAMBRIDGE STREET bull SUITE 201 bull 8URUNGTON MA 01803 bull TEL 617-273-9080 bull FAX 617-273-90W
07151996 18 fO 6179444082 CASHINS S ASSOCIATES PAGE 02
CASHINS amp Associates Inc
WBBKLY HEALTH amp SAFETY FLAK COMPLIANCE SUMMARY REPORT
CLIENT T Ford Compapv
LOCATION i Sal am Acrlaquolaquo Suparfund Sita SL-4 Area
DATES INCLUDED IN SUMMARY i bull pound7 mdash
A 0-3 - A)
SXWMARIZ2D BY FOR CASHINS amp ASSOCIATES INC (
55 CAMBRIDGE STREET SUITE 201 bull SURtlNCTON MA 01803 TEL 617-273-9080 bull FAX 61 7-273-9084
- barcode 14732
- barcodetext SEMS Doc ID 14732
![Page 66: SALEM ACRES SUPERFUND SITE SALEM, MA ...The truck loading pa d consisted of a crushed stone are sea t up along the east sid e o f SL-4 adjacent to the access road A. row of concrete](https://reader036.vdocuments.us/reader036/viewer/2022070114/60729b840fec4e6b4d136a16/html5/thumbnails/66.jpg)
CASHIMS amp ASSOCIATES PAGE 04 07161996 1658 6179444032
OVSHINSamp Associates Inc
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT
CLIENT T Ford Company T
LOCATION Salem AcrM Suoerfund Stta 8L-4 Araa
DATES INCLUDED IN SUMMARY
(7
ft ^ 0
SUMMARIZED BY pound FOR CASHINS amp ASSOCIATES INC
55 CAMBRIDGE STREET bull SUITE 201 bull BURUNGTON MA 01803 bull TEL 617-273-9080 bull FAX 617-273-9084
07161996 1658 6179444082 CASHIMS 3 ASSOCIATES PAGE 03
CASHINSamp Associates Inc
ndurtrW Hrtnm t
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT ^
CLIENT T Ford Company t lP ~ ff2-r
LOCATION Sal era Acraa Suplaquorfund Sj-ta 8L-4 Araa
DATES INCLUDED IN SUMMARY
if
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SUMMARIZED BY FOR CASMINS amp ASSOCIATES INC
55 CAMBRIDGE STREET bull SUITE 201 bull 8URUNGTON MA 01803 bull TEL 617-273-9080 bull FAX 617-273-90W
07151996 18 fO 6179444082 CASHINS S ASSOCIATES PAGE 02
CASHINS amp Associates Inc
WBBKLY HEALTH amp SAFETY FLAK COMPLIANCE SUMMARY REPORT
CLIENT T Ford Compapv
LOCATION i Sal am Acrlaquolaquo Suparfund Sita SL-4 Area
DATES INCLUDED IN SUMMARY i bull pound7 mdash
A 0-3 - A)
SXWMARIZ2D BY FOR CASHINS amp ASSOCIATES INC (
55 CAMBRIDGE STREET SUITE 201 bull SURtlNCTON MA 01803 TEL 617-273-9080 bull FAX 61 7-273-9084
- barcode 14732
- barcodetext SEMS Doc ID 14732
![Page 67: SALEM ACRES SUPERFUND SITE SALEM, MA ...The truck loading pa d consisted of a crushed stone are sea t up along the east sid e o f SL-4 adjacent to the access road A. row of concrete](https://reader036.vdocuments.us/reader036/viewer/2022070114/60729b840fec4e6b4d136a16/html5/thumbnails/67.jpg)
07161996 1658 6179444082 CASHIMS 3 ASSOCIATES PAGE 03
CASHINSamp Associates Inc
ndurtrW Hrtnm t
WEEKLY HEALTH amp SAFETY PLAN COMPLIANCE SUMMARY REPORT ^
CLIENT T Ford Company t lP ~ ff2-r
LOCATION Sal era Acraa Suplaquorfund Sj-ta 8L-4 Araa
DATES INCLUDED IN SUMMARY
if
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SUMMARIZED BY FOR CASMINS amp ASSOCIATES INC
55 CAMBRIDGE STREET bull SUITE 201 bull 8URUNGTON MA 01803 bull TEL 617-273-9080 bull FAX 617-273-90W
07151996 18 fO 6179444082 CASHINS S ASSOCIATES PAGE 02
CASHINS amp Associates Inc
WBBKLY HEALTH amp SAFETY FLAK COMPLIANCE SUMMARY REPORT
CLIENT T Ford Compapv
LOCATION i Sal am Acrlaquolaquo Suparfund Sita SL-4 Area
DATES INCLUDED IN SUMMARY i bull pound7 mdash
A 0-3 - A)
SXWMARIZ2D BY FOR CASHINS amp ASSOCIATES INC (
55 CAMBRIDGE STREET SUITE 201 bull SURtlNCTON MA 01803 TEL 617-273-9080 bull FAX 61 7-273-9084
- barcode 14732
- barcodetext SEMS Doc ID 14732
![Page 68: SALEM ACRES SUPERFUND SITE SALEM, MA ...The truck loading pa d consisted of a crushed stone are sea t up along the east sid e o f SL-4 adjacent to the access road A. row of concrete](https://reader036.vdocuments.us/reader036/viewer/2022070114/60729b840fec4e6b4d136a16/html5/thumbnails/68.jpg)
07151996 18 fO 6179444082 CASHINS S ASSOCIATES PAGE 02
CASHINS amp Associates Inc
WBBKLY HEALTH amp SAFETY FLAK COMPLIANCE SUMMARY REPORT
CLIENT T Ford Compapv
LOCATION i Sal am Acrlaquolaquo Suparfund Sita SL-4 Area
DATES INCLUDED IN SUMMARY i bull pound7 mdash
A 0-3 - A)
SXWMARIZ2D BY FOR CASHINS amp ASSOCIATES INC (
55 CAMBRIDGE STREET SUITE 201 bull SURtlNCTON MA 01803 TEL 617-273-9080 bull FAX 61 7-273-9084
- barcode 14732
- barcodetext SEMS Doc ID 14732