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REMEDIAL INVESTIGATION WORK PLAN
for
PROPOSED 363 BOND STREET REDEVELOPMENT
Brooklyn, New York Tax Map Block 452 Lots 1 & 15
NYCOER Project No. 13EH-A196K
NYSDEC Spill Nos. 05-01697 & 04-00876
USEPA No. 422395.DE.02
Prepared For:
The Lightstone Group 460 Park Avenue, 13th Floor
New York, New York 10022
Prepared By:
Langan Engineering, Environmental, Surveying
and Landscape Architecture, D.P.C. 619 River Drive Center 1
Elmwood Park, New Jersey 07407 NJ Certificate of Authorization No. 24GA27996400
Chris McMahon
Project Geologist
Steven A. Ciambruschini, PG, LEP
Principal / Vice President
Final: 9 November 2012
Final Revised: 10 July 2013
100287501
Remedial Investigation Work Plan Proposed 363 Bond Street Development
TOC-i
TABLE OF CONTENTS
1.0 INTRODUCTION ............................................................................................................. 1
1.1 Site Location and Current Usage ...................................................................... 1
1.2 Proposed Redevelopment Plan ......................................................................... 2
1.3 Description of Surrounding Property ............................................................... 3
2.0 PREVIOUS ENVIRONMENTAL DOCUMENTATION ..................................................... 3
2.1 Environmental Investigation Reports ............................................................... 3
2.2 Summary of Regulatory Correspondence ........................................................ 4
2.3 Findings of Previous Environmental Investigations ........................................ 6
2.4 Data Usability ................................................................................................... 18
2.5 Summary of Previous Environmental Investigations .................................... 19
3.0 PHASE II ENVIRONMENTAL INVESTIGATION .......................................................... 26
3.1 Investigation Rationale .................................................................................... 26
3.2 Investigation Procedures ................................................................................. 28
3.3 Sample Analysis ............................................................................................... 31
3.4 Reporting .......................................................................................................... 31
4.0 QUALITY ASSURANCE/QUALITY CONTROL ............................................................ 32
4.1 Quality Assurance/Quality Control Procedures ............................................. 32
4.2 Field QA/QC ..................................................................................................... 32
4.3 Sample Custody ............................................................................................... 33
4.4 Report Logs ...................................................................................................... 34
4.5 Laboratory QA/QC ........................................................................................... 35
5.0 HEALTH AND SAFETY PLAN (HASP) ......................................................................... 36
5.1 Health and Safety Plan (HASP) ....................................................................... 36
Remedial Investigation Work Plan Proposed 363 Bond Street Development
TOC-ii
TABLES
Table 1 Historic Sampling Summary
Table 2 Historic Soil Analytical Results – 363 Bond Street
Table 3 Historic Groundwater Analytical Results – 363 Bond Street
Table 4 Historic Soil Vapor Analytical Results – 363 Bond Street
Table 5 Historic Soil Analytical Results – 400 Carroll Street
Table 6 Historic Groundwater Analytical Results – 400 Carroll Street
Table 7 Proposed Remedial Investigation Sampling Summary
FIGURES
Figure 1 Site Location Map
Figure 2 Site Plan
Figure 3 Summary of Historic Soil Analytical Data – 363 Bond Street
Figure 4 Summary of Historic Groundwater Analytical Data – 363 Bond Street
Figure 5 Summary of Historic Soil Vapor Analytical Data – 363 Bond Street
Figure 6 Summary of Historic Soil Analytical Data – 400 Carroll Street
Figure 7 Summary of Historic Groundwater Analytical Data – 400 Carroll Street
Figure 8 Summary of NAPL Observations
Figure 9 Proposed Sample Location Plan
APPENDICES
Appendix A Architectural Drawings
Appendix B Previous Environmental Investigations
Appendix C Previous Regulatory Correspondence
Appendix D HASP
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11-09, Rev.2013-07-10).doc
Remedial Investigation Work Plan Proposed 363 Bond Street Development
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Acronym Definition
AST Aboveground Storage Tank
CAMP Community Air Monitoring Plan
C&D Construction & Demolition
CEQR City Environmental Quality Review
CFR Code of Federal Regulations
CHASP Construction Health and Safety Plan
CO Certificate of Occupancy
CPC City Planning Commission
DSNY Department of Sanitation
“E” E-Designation
EAS Environmental Assessment Statement
EIS Environmental Impact Statement
ESA Environmental Site Assessment
EC/IC Engineering Control and Institutional Control
ELAP Environmental Laboratory Accreditation Program
FDNY New York City Fire Department
GPR Ground Penetrating Radar
HASP Health and Safety Plan
HAZWOPER Hazardous Waste Operations Emergency Response
IDW Investigation Derived Waste
Notice - NNO Notice of No Objection
Notice - NTP Notice To Proceed
Notice - NOS Notice Of Satisfaction
Notice - FNOS Final Notice of Satisfaction
NYC BSA New York City Board of Standards and Appeals
NYC DCP New York City Department of City Planning
NYC DEP New York City Department of Environmental Protection
NYC DOB New York City Department of Buildings
NYC DOF New York City Department of Finance
NYC HPD New York City Housing Preservation and Development
NYCRR New York Codes Rules and Regulations
NYC OER New York City Office of Environmental Remediation
Remedial Investigation Work Plan Proposed 363 Bond Street Development
TOC-iv
Acronym Definition
NYS DEC New York State Department of Environmental Conservation
NYS DEC DER New York State Department of Environmental Conservation
Division of Environmental Remediation
NYS DEC PBS New York State Department of Environmental Conservation
Petroleum Bulk Storage
NYS DOH New York State Department of Health
NYS DOT New York State Department of Transportation
OSHA United States Occupational Health and Safety Administration
PAHs Polycyclic Aromatic Hydrocarbons
PCBs Polychlorinated Biphenyls
PE Professional Engineer
PID Photo Ionization Detector
PM Particulate Matter
QEP Qualified Environmental Professional
RA Register Architect
RAP Remedial Action Plan
RCA Recycled Concrete Aggregate
RCR Remedial Closure Report
RD Restrictive Declaration
RI Remedial Investigation
SCOs Soil Cleanup Objectives
SCG Standards, Criteria and Guidance
SMP Site Management Plan
SPDES State Pollutant Discharge Elimination System
SSDS Sub-Slab Depressurization System
SVOCs Semi-Volatile Organic Compounds
USCS Unified Soil Classification System
USGS United States Geological Survey
UST Underground Storage Tank
TAL Target Analyte List
TCL Target Compound List
TCO Temporary Certificate of Occupancy
VB Vapor Barrier
VOCs Volatile Organic Compounds
Remedial Investigation Work Plan Proposed 363 Bond Street Development
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1.0 INTRODUCTION
This Remedial Investigation Work Plan (RIWP) and Health and Safety Plan (HASP)
have been developed for the Proposed 363 Bond Street Redevelopment project,
located at 363 Bond Street (Block 452 Lot 1) and 400 Carroll Street (Block 452
Lot 15) in the Carroll Gardens neighborhood of Brooklyn, New York (the Site).
Remedial Investigation and Remedial Action Work Plan (RAWP) were previously
reviewed and approved by the New City Department of Environmental Protection
(NYCDEP) and New York State Department of Environmental Conservation
(NYSDEC) for the Site. In addition, the United States Environmental Protection
Agency (USEPA) has reviewed and accepted a RIWP and conceptual RAWP for
400 Carroll Street. This Work Plan describes the proposed investigation that will
address the environmental concerns identified in previous Phase I ESAs and
supplement the results reported during previous sub-surface investigations. This
investigation is being conducted to complete delineation of the previously defined
excavation and/or soil stabilization areas as identified in the 2009 Remedial Action
Plan (RAP) (previously approved by NYSDEC) prepared for the Site. Additional soil,
groundwater and soil gas sampling was completed subsequent to the RAP submittal
as part of a due diligence assessment of the Site, and additional sampling is
proposed as part of this work plan to address NYSDEC requirements for delineation
and assessment of groundwater and soil gas in order to develop a revised Remedial
Action Work Plan. The investigation activities being completed as part of this
remedial investigation (in addition to the results of the previous investigations) will
completely delineate areas where excavation of impacted soil will be conducted and
seek to define the final limits of these excavations. A detailed discussion of
previous report submittals and results of the due diligence investigation are
provided in Section 2.0 of this work plan.
The site-specific HASP, which includes a Community Air Monitoring Plan (CAMP),
(Appendix D) addresses potential hazards, contaminants of concern based on past
use and safety requirements associated with investigation activities in accordance
with ASTM and OSHA guidelines.
1.1 Site Location and Current Usage
The Site is located in the Carroll Gardens neighborhood of Brooklyn, New York
and is identified as Block 452, Lots 1 and 15 on the New York City Tax Map.
Figure 1 is a Site location map and a site plan of the properties is provided as
Figure 2. The Site consists of the two parcels as discussed below.
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The property at 363 Bond Street (Tax Block 452, Lot 1) is located east of the
intersection of Bond Street and First Street in Brooklyn, New York. The
approximately ±0.68-acre site contains a one- and two-story light industrial
building. The site is bounded to the northeast by a two-story mixed-use
commercial and residential building associated with the 400 Carroll Street
subject property and a one-story building and associated parking that is operated
by the City of New York as an EMS station, (located along Carroll Street), to the
southeast by the Gowanus Canal followed by a one-story industrial and
manufacturing building, to the southwest by First Street followed by a two-story
commercial building, and to the northwest by Bond Street followed by a three-
story mixed-use commercial and residential building and a six-story residential
building.
The property at 400 Carroll Street (Tax Block 452, Lot 15) is located southeast of
the intersection of Carroll Street and the Gowanus Canal. The site is
approximately ±0.67-acres. The site is improved with a two-story, residential
building. In addition, two vacant secondary containment structures for the
former aboveground storage tanks (ASTs) remain on the property. The site is
bounded to the northeast by Carroll Street followed by a four-story industrial and
manufacturing building and associated parking lot, to the southeast by the
Gowanus Canal followed by a one-story industrial and manufacturing building, to
the southwest by the subject property at 363 Bond Street, and to the northwest
by a one-story building and associated parking that is operated by the City of
New York as an EMS station and a two-story residential building.
1.2 Proposed Redevelopment Plan
The proposed use of the Site will consist of constructing a 5- to 12-story
residential building occupying almost the entire footprint of the subject
properties. The first floor levels of the buildings will be occupied by parking
garages and residential and commercial spaces. A partial below-grade parking
level is currently proposed in a portion of the Site. In addition to the building
plans, a waterfront esplanade will be developed along the Gowanus Canal
shoreline. The subject properties are zoned as M1-4/R7-2, industrial and
manufacturing and medium-density apartment house residential. Additionally,
the subject properties are zoned in a Special Mixed Use District established to
encourage the investment in and enhance the vitality of existing neighborhoods
Remedial Investigation Work Plan Proposed 363 Bond Street Development
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with mixed residential and industrial uses in close proximity. A copy of the
architectural plans for the Site is provided in Appendix A.
1.3 Description of Surrounding Property
The surrounding area consists of industrial, commercial, and residential uses. A
residential building, an EMS station, and commercial and manufacturing
buildings are located to the north of the subject properties. Commercial,
industrial, and manufacturing buildings are located to the south of the subject
properties. To the east is the Gowanus Canal followed by industrial facilities.
Bond Street is located to the west of the subject properties followed by multi-
family residential buildings. The majority of surrounding properties have a
M1-4/R7-2, industrial and manufacturing zoning designation or a R6B, mixed
residential and commercial building zoning designation.
2.0 PREVIOUS ENVIRONMENTAL DOCUMENTATION
2.1 Environmental Investigation Reports
The following environmental work plans and reports were developed for the
subject properties:
Soil Investigation - 400 Carroll Street, dated November 1997, prepared by
Cosmos Environmental Services;
Soil Sampling Report – 400 Carroll Street, dated September 2002,
prepared by Tradewinds;
Environmental Investigation – 400 Carroll Street, October 2002, prepared
by North Atlantic;
Phase II Investigation Report – 400 Carroll Street, dated May 6, 2005,
prepared by ELM;
Phase II Investigation Report – 363 Bond Street, dated May 31, 2005,
prepared by ELM;
Remedial Action Plan – 363-365 Bond Street and 400 Carroll Street,
dated February 3, 2009, Prepared by ELM;
Draft Subsurface Investigation Summary Report, dated 13 September 2011,
prepared by PW Grosser Consulting, Inc.;
Remedial Action Plan – 400 Carroll Street, dated July 2011, prepared by
PW Grosser Consulting, Inc.;
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Bulkhead Replacement – 400 Carroll Street letter, dated 25 October 2011,
prepared by PW Grosser;
Phase I Environmental Assessment – 363 Bond Street, dated February 2012,
prepared by PW Grosser;
Phase I Environmental Assessment – 400 Carroll Street, dated February 2012,
prepared by PW Grosser;
Soil Sampling – 400 Carroll Street, dated April 2012, completed by Zeb
Environmental; and,
Limited Phase II Environmental Investigation Report – Proposed 363-365 Bond
Street Redevelopment, dated October 2012, completed by Langan
Engineering & Environmental Services.
Digital copies of the above referenced environmental work plans and reports
are included in Appendix B.
2.2 Summary of Regulatory Correspondence
The following is a summary of pertinent regulatory correspondence related
to the subject properties:
Notice of Completion of the Final Environmental Impact Statement, prepared by
the New York City Department of City Planning, dated 6 February 2009.
The New York City Department of City Planning issued the Notice of
Completion of the Final Environmental Impact Statement that was submitted
for the redevelopment of 363 Bond Street and 400 Carroll Street.
Remedial Action Plan Approval Letter, prepared by the New York State
Department of Environmental Conservation, dated 19 July 2011. In a letter
dated 19 July 2011, the NYSDEC approved the Revised Remedial Action Plan
submitted by P.W. Grosser Consulting, Inc on behalf of Wooden Bridge, LLC.
The revised remedial plan proposed the excavation and offsite disposal of
petroleum-contaminated soils from three “hot spot” areas which were
previously intended for soil stabilization.
Email dated 40 March 2012, RE: 400 Carroll Street, from Brian Carr (USEPA)
to David Yudelson (Sive, Paget & Riesel, P.C.)
This email identifies that the conceptual bulkhead replacement proposed by
PW Grosser was reviewed and, that the conceptual approach was approved.
Remedial Investigation Work Plan Proposed 363 Bond Street Development
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It is further identified that formal approval would be contingent on review of
a detailed design.
In a letter dated September 2012, the USEPA issued a letter regarding the
Lightstone Group proposal at the former Toll Brothers property. The letter
identifies that groundwater monitoring wells were installed on the
400 Carroll Street property to assess the former location of two fuel
terminals. The results identified an area of deep subsurface contamination at
the 400 Carroll Street property and that additional sampling be completed at
this property to address these impacts. Additional sampling was completed
in 2011 and the results indicated small localized deep impacts that would not
impact the future redevelopment of the site.
October 2012 EPA Update Regarding the Lightstone Group Proposal,
prepared by the USEPA.
This letter identified that the USEPA’s conceptual approach to a coordinated
cleanup includes:
1. Addressing continuing upland sources before dredging of the Canal to
be conducted as part of the overall Superfund Cleanup, reaches that
location;
2. Where possible, upgrading bulkheads before dredging to reduce the
cost and time needed to install temporary sheet piling; and,
3. Reducing the impacts of Combined Sewer Overflow discharges.
The letter notes that the proposed redevelopment of the site would satisfy
each of these goals if implemented.
Phase I ESA Summary
363 Bond Street
The Phase I ESA completed by PW Grosser in February 2012 identified the
following recognized environmental concerns (RECs):
The property’s extensive industrial history;
Historical underground gasoline tanks with potential vent pipes;
An existing aboveground fuel oil tank in the basement;
An active NYSDEC spill and free phase petroleum in the water table;
Historic fill;
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Location adjacent to the Gowanus Canal, a National Priorities List (Superfund)
site; and,
E-designation, E-221, for air quality.
400 Carroll Street
The Phase I ESA completed by PW Grosser in February 2012 identified the
following RECs:
The property’s extensive industrial history;
Historical underground gasoline tanks;
An active NYSDEC spill with the presence of contaminated soil and
groundwater and potential for sub-slab vapor/indoor air concern;
Historic fill;
Location adjacent to the Gowanus Canal, a National Priorities List (Superfund)
site; and,
E-designation, E-221, for air quality.
2.3 Findings of Previous Environmental Investigations
The following previous environmental reports were completed for the subject
property. RECs/AOCs identified in these reports are shown on Figure 2 and a
historic sampling summary table is provided as Table 1. Historic soil,
groundwater, and soil vapor results for 363 Bond Street are shown on Figures 3,
4, and 5, respectively and on Figures 6, and 7, respectively for 400 Carroll Street.
Historic soil analytical results (compared to current NYSDEC Brownfields Soil
Cleanup Objectives (SCOs) for 363 Bond Street and 400 Carroll Street are
summarized on Tables 2 and 5, respectively and historic groundwater analytical
results for these parcels are summarized in Tables 3 and 6, respectively.
Historic soil vapor analytical results for 363 Bond Street are provided in Tables 4.
Details of the previous environmental investigation reports are provided below.
Geology and Hydrogeology
Based on the observations made during the previous investigation completed
at the Site, the entire Site is underlain by a layer of miscellaneous fill material
that is underlain by a continuous clay layer. A description of the thickness of
the fill material and clay layer as well as groundwater observations for each
property is provided below.
Remedial Investigation Work Plan Proposed 363 Bond Street Development
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363 Bond Street
The site is underlain by a 6- to 17-foot thick layer of miscellaneous fill material.
The fill material is underlain by a clay layer that was identified in each of the
borings completed. The clay layer was observed to be approximately 4 feet
thick in two of the Langan borings (LSB-3 and LSB-4), and greater than 4 feet
thick at the LSB-1 and LSB-2 locations. Groundwater was observed in each of
the boring locations at depths ranging from approximately 1.25 to 7.5 feet below
ground surface (bgs).
400 Carroll Street
The site is underlain by an approximately 6- to 8-foot thick layer of miscellaneous
fill material that was underlain by a clay layer that was observed in all of the
borings and test pits that were advanced. The the thickness of the clay layer on
this parcel has not been identified. Groundwater at the site was observed
between 5 to 10 feet bgs
363 Bond Street
Phase II Investigation Report – 363 Bond Street, dated May 31, 2005,
prepared by ELM
1. Soil was noted to be saturated with light non-aqueous phase liquid (LNAPL)
in soil borings MW-5 (7 to 7.5 feet bgs and 8 to 12 feet bgs) and SB-1 (4 to
4.5 feet bgs) and LNAPL was encountered in monitoring wells MW-3 (6
inches thick) and MW-5 (1 inch thick).
2. Elevated concentrations of volatile organic compounds (VOCs) (benzene,
2-butanone, toluene, and total xylenes) above the NYSDEC Technical
Administrative Guidance Memo (TAGM) 4046 Recommended SCOs (RSCOs)
were noted in soil samples collected at MW-3 (4 to 6 feet bgs), MW-5 (7.5 to
9.5 feet bgs), SB-1 (4 to 6 feet bgs), SB-3 (6 to 8 feet bgs), and SB-4 (9 to
10.5 feet bgs). Polycyclic aromatic hydrocarbons (PAHs) and napthalene
were detected in deep vadose and saturated zones above the TAGM RSCOs
at MW-2, MW-4, MW-5, SB-2 SB-4, and SB-5 and in the vadose zone in
MW-3, SB-1 and SB-3. Pesticides (dieldrin and heptachlor epoxide) were
detected in soil above the TAGM RSCOs at MW-2 (1 to 3 feet bgs), MW-5
(7.5 to 9.5 feet and 13 to 15 feet bgs), and SB-1 (1 to 4 feet bgs). Metals
(arsenic, barium, cadmium, calcium, chromium, copper, iron, lead,
magnesium, manganese, mercury, nickel, selenium, and zinc) were detected
Remedial Investigation Work Plan Proposed 363 Bond Street Development
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in soil in the deep vadose and saturated zones above the TAGM 4046 RSCOs
in MW-1, MW-2, MW-3, MW-4, MW-5, SB-1, SB-2, SB-3, SB-4, and SB-5.
Polychlorinated biphenyls (PCBs) were not detected in soil above the TAGM
RSCOs.
3. Elevated concentrations of VOCs (benzene, toluene, ethylbenzene, total
xylenes, and vinyl chloride) above the NYSDEC Ground Water Quality
Standards (GWQS) were detected in groundwater at MW-4 and MW-5.
Semi-volatile organic compounds (SVOCs) (naphthalene, acenaphthene,
benzo(a)anthracene, benzo(a)pyrene, chrysene, dibenzofuran, fluorine,
2-methylnaphthalene, 2-methylphenol, phenanthrene, and phenol) were
detected above GWQS at MW-2 and MW-5. Total and dissolved metals
(arsenic, cadmium, iron, lead, manganese, and sodium) were detected above
GWQS in all four of the samples collected. Pesticides and PCBs were not
detected above the Part 703 GWQS in any of the groundwater samples
collected.
4. Langan compared the soil analytical data from the 2005 sampling to the
NYSDEC SCOs. Elevated concentrations of VOCs (acetone, benzene,
ethylbenzene, 2-butanone, methylene chloride, toluene, vinyl chloride, and
total xylenes) above the Unrestricted Use Objectives (UUOs) were
detected in MW-2 (1 to 3 feet bgs), MW-3 (4 to 6 feet bgs), MW-5 (7.5 to
9.5 feet bgs), SB-1 (1 to 4 feet bgs), SB-3 (6 to 8 feet bgs), and SB-4 (9 to
10.5 feet bgs). Additionally, elevated concentrations of benzene were
detected above the Residential Use Objectives (Residential UOs) in SB-3 (4
to 6 feet bgs). A summary of SVOC and metal exceedances is provided in
the table below.
Remedial Investigation Work Plan Proposed 363 Bond Street Development
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Boring
Location
Depth
(feet
bgs)
Parameters UUOs Residential
RUOs
Restricted
Residential
RUOs
Restricted
Commercial
RUOs
Restricted
Industrial
RUOs
MW-2 1 to 3 PAH/Metals X X X X X
MW-2 9 to 10 PAH X X X X
MW-2 9 to 10 Metals X X X
SB-1 1 to 4 PAH X X X X X
SB-1 1 to 4 Metals X X X
SB-1 10 to 12 Metals X
SB-2 6 to 8 Metals X X
SB-2 10 to 12 PAH X X X X X
SB-2 10 to 12 Metals X X X X
SB-3 6 to 8 PAH X X X X X
SB-3 6 to 8 Metals X X X
SB-4 9 to 10.5 PAH X X X X X
SB-4 9 to 10.5 Metals X X X X
SB-5 7 to 8 PAH/Metals X X X X X
MW-5 7.5 to 9.5 PAH/Metals X X X X X
MW-5 13- to 15 PAH X X X X X
MW-5 13- to 15 Metals X
MW-4 6 to 8 Metals X X X X X
MW-4 12 to 14 Metals X X X
Pesticides (4,4’-DDE, 4-4’-DDT, and aldrin) were detected above the UUOs in
MW-4 (12 to 14 feet bgs), MW-5 (7.5 to 9.5 feet and 13 to 15 feet bgs), SB-3 (6
to 8 feet bgs), and SB-4 (9 to 10.5 feet bgs). Dieldrin was detected above the
Residential RUOs in MW-2 (1- to 3 feet bgs). PCBs (Arochlor 1254) above the
UUOs were detected in SB-4 4 (9 to 10.5 feet bgs).
Remedial Investigation Work Plan Proposed 363 Bond Street Development
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400 Carroll Street
Soil Investigation - 400 Carroll Street, dated November 1997, prepared
by Cosmos Environmental Services
1. Photoionization detector (PID) readings during soil screening detected
elevated readings from 89 to 177 parts per million (ppm).
2. LNAPL was not noted during this investigation.
3. Groundwater was encountered approximately 8 to 10 feet below grade.
4. Analytical results showed elevated levels of VOCs and SVOCs in the soil
and groundwater above the NYSDEC TAGM 4046 RSCOs for soil and the
NYSDEC GWQS for groundwater. VOCs detected in soil and
groundwater at the site included benzene, ethylbenzene, toluene,
xylenes (BTEX), and naphthalene.
5. Langan compared the soil analytical data collected by Cosmos to the
NYSDEC SCOs dated 14 December 2006. Elevated concentrations of
VOCs (benzene, ethylbenzene, propylbenzene-n, toluene, o-xylene, p-
xylene, and total xylenes) were detected above the UUOs in TP-1, TP-3,
TP-6, TP-7, and TP-8. SVOCs consisting primarily of PAHs were detected
above the UUOs in TP-3, the Residential RUOs in TP-1, TP-3, and TP-8,
the Restricted Residential RUOs in TP-1, TP-3 and TP-8, the Restricted
Commercial RUOs in TP-8, and the Restricted Industrial RUOs in TP-1,
TP-3 and TP-8. Elevated concentrations of mercury were detected above
the Restricted Residential RUOs in the composite soil sample.
Phase II Investigation Report – 400 Carroll Street, dated May 6, 2005,
prepared by ELM
1. The highest PID reading was observed in boring SB-6/TW at the 4 to 5
foot interval.
2. Petroleum odors and sheen on groundwater were noted during purging
of the wells during the sampling program at all well locations except
MW-1.
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3. Elevated concentrations of VOCs (benzene, ethylbenzene, and total
xylenes) above the NYSDEC TAGM 4046 RSCOs were noted in soil at SB-1
(4 to 5 feet bgs), SB-3 (5 to 7 feet bgs), SB-4 (3 to 5 feet bgs), SB-8 (5 to
7 feet bgs), TP-5 (1.5 to 3 feet bgs), and TP-6 (2.7 to 4.7 feet bgs). Additional
VOCs (acetone and methylene chloride) were detected in the majority of the
soil samples collected but were attributed to laboratory artifacts. PAHs
(benzo(a)anthracene, benzo(a)pyrene, benzo(b)fluoranthene, benzo(k)fluoranthene,
chrysene, dibenzo(a,h)anthracene, and indeno(1,2,3-cd)pyrene)PAHs were
detected in soils in the shallow and deep vadose zones above the TAGM
4046 RSCOs at SB-1, SB-3, SB-4,SB-6, SB-8 , SB-9, SB-10, SB-11, SB-12, TP-1,
TP-3, TP-4, TP-5, and TP-6. Metals (arsenic, beryllium, cadmium, calcium,
chromium, iron, lead, magnesium, manganese, mercury, nickel, selenium, and
zinc) were detected in soil above the TAGM 4046 RSCOs in all nineteen soil
samples. PCBs were not detected in soil above the TAGM 4046 RSCOs.
4. Elevated concentrations of VOCs (benzene, toluene, and total xylenes) above
the NYSDEC GWQS were detected in groundwater at MW-1, SB-2/TW,
SB-3/TW, SB-6/TW, and SB-11/TW. PAHs) were detected above GWQS at
SB-7/TW and SB-11/TW and total PCBs were detected above GWQS at
SB-7/TW. Dissolved metals (antimony, iron, magnesium, manganese, and
sodium) were detected above the GWQS in all seven of the samples
collected.
5. Langan compared the soil analytical data collected by ELM to the NYSDEC
Brownfields SCOs. VOCs (acetone, benzene, ethylbenzene, methylene
chloride, toluene, and total xylenes) were detected above the UUOs at SB-1
(4 to 5 feet bgs), SB-3 (5 to 7 feet bgs), SB-4 (3 to 5 feet bgs), SB-6 (4 to 6
feet bgs), SB-8 (5 to 7 feet bgs), SB-9 (3 to 5 feet bgs), SB-10 (1 to 3 feet
bgs), SB-11 (4 to 5 feet bgs), TP-1 (0.5 to 3 feet and 3 to 3.5 feet bgs), TP-3
(4 to 7 feet bgs), TP-4 (4 to 5 feet bgs), TP-5 (1.5 to 3 feet bgs), and TP-6 (2.7
to 4.7 feet bgs). A summary of SVOC and metal exceedances is provided in
the table below.
Remedial Investigation Work Plan Proposed 363 Bond Street Development
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Boring
Location
Depth
(feet
bgs)
Parameters UUOs Residential
RUOs
Restricted
Residential
RUOs
Restricted
Commercial
RUOs
Restricted
Industrial
RUOs
SB-1 4 to 5 PAH X X X X X
SB-10 1 to 3 PAH X X X X X
TP-5 1.5 to 3 PAH X X X X X
SB-9 3 to 5 PAH X X X X X
SB-11 4 to 5 PAH X X X X X
SB-1 4 to 5 Metals X X X
SB-3 5 to 7 Metals X X X X X
SB-4 3 to 5 Metals X
SB-6 4- to 6 Metals X X X
SB-8 5- to 7 Metals X
SB-10 1- to 3 Metals X
SB-11 4- to 5 Metals X
SB-12 2- to 4 Metals X
TP-1 0.5- to 3 Metals X X X X X
TP-3 4- to 7 Metals X
TP-5 1.5- to 3 Metals X X X
TP-6 2.7 to 4.7 Metals X X X X X
Elevated concentrations of PCBs were detected above the UUOs at SB-1 (4
to 5 feet bgs).
Remedial Action Plan – 363-365 Bond Street and 400 Carroll Street,
dated 3 February 2009, prepared by ELM
This Remedial Action Plan (RAP) was prepared on behalf of Toll Gowanus, LLC
and was submitted to both the NYCDEP and the NYSDEC. The RAP was
prepared to allow for the redevelopment of the property in accordance with
the City Environmental Quality Review (CEQR) process and the
Environmental Impact Statement for the Site. The RAP was based on the
above identified Phase II investigations that were completed at all three
properties. The proposed remedial actions were designed to address “hot-
spots” of petroleum-related VOCs and SVOCs, and PAHs associated with
the historic urban fill. Additionally, the proposed remedy would also address
the LNAPL “hot-spot” that was identified at the 363 Bond Street property.
Remedial Investigation Work Plan Proposed 363 Bond Street Development
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Specifically, the proposed remedy included the removal of soil in areas
where LNAPL was encountered at 363 Bond Street to a depth of 2 feet
below the groundwater table or approximately 7 feet bgs. The proposed
area to be excavated was approximately 1,250 square feet; however, a
contingency was provided for expanding the excavation area until free phase
petroleum was no longer encountered. All excavated soils would be
disposed of off-site.
Two alternatives for in-situ remediation, soil stabilization or chemical
treatment of “hot-spots”, at the 400 Carroll Street and 363 Bond Street sites
was also proposed. The method of soil stabilization proposed was to mix
the soils with portland cement and bentonite clay and the effectiveness of
this remedy was to be evaluated using a bench-scale mixing study and post-
remedial sampling of the stabilized mass. The RAP proposed that soil
stabilization would be completed from the surface to 7 feet bgs (elevation
corresponding to 2 feet into the groundwater table).
Pending the results of the soil-stabilization bench-scale study which would
determine the viability of this remedy, a second in-situ remedy of chemical
oxidation was proposed if soil-stabilization would not sufficiently address the
contaminants in the “hot-spots”. The specific oxidation agent identified for
the site was RegenOx which uses sodium percarbonate to oxidize the
petroleum contamination. The proposed application would be applied from
ground surface to 7 feet bgs, the results of the remedy would be monitored
via groundwater effectiveness monitoring.
In order to address potential soil vapor intrusion risks, the RAP proposed the
installation of a soil vapor barrier and sub-slab depressurization system. The
vapor barrier was specified to be a 15-mil GSE brand geomembrane. A
passive sub-slab depressurization system was proposed beneath both of the
proposed buildings.
Additionally, the engineering control of site capping was also identified as
one of the site remedies. It was identified that the entire site would be
capped by building foundations, concrete/asphalt walkways and sidewalks
and landscaped areas. The landscaped areas were to be capped with 2 feet
of clean fill from a certified clean fill source that would be underlain by a high
visibility demarcation barrier.
Remedial Investigation Work Plan Proposed 363 Bond Street Development
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Remedial Action Plan – 400 Carroll Street, dated July 2011, prepared by
PW Grosser Consulting, Inc.
This RAP was prepared for Wooden Bridge, LLC for the 400 Carroll Street
property based on the data provided in the ELM report that was discussed in
detail above. The RAP proposed excavation and offsite soil disposal as the
only remedy for the three “hot-spots” that were identified as potential soil-
stabilization areas in the 2009 ELM RAP. As previously proposed,
excavations would extend to approximately 7 feet bgs and excavation areas
would be properly contained with soil erosion and sediment controls prior to
the excavations.
The proposed excavation extents were to be determined based on visual,
olfactory and photoionization detector (PID) evidence that no petroleum
impacts exist. Additionally, end-point samples were proposed from each
sidewall of the excavation areas to determine that the excavation has
removed all petroleum impacted material. No bottom samples were
proposed based on the removal of all material to the underlying clay layer
based on documentation that the clay layer has not been impacted by
petroleum impacts.
Draft Subsurface Investigation Summary Report – 400 Carroll Street,
dated September 2011, prepared by PW Grosser Consulting, Inc.
1. This investigation was completed in order to assess the potential that the
400 Carroll Street property was a contributor of deep (approximately 25 to 30
feet bgs) coal tar impacts to the Gowanus Canal. Deep impacts were
reported as part of the USEPA remedial investigation of the sediments within
the canal adjacent to the property. All borings were advanced to a depth of
approximately 35 feet bgs as part of this investigation.
2. Thin lenses of impacted soil containing NAPL were observed in three of the
nine soil samples (GP-01, GP-05, and GP-08) approximately 25 feet below
ground surface located to the east of MW-43 (between MW-43 and the
Gowanus Canal).
3. A soil sample was collected from GP-05 for the fingerprint identification
of the free product. The sample was identified as coal tar/creosote,
Remedial Investigation Work Plan Proposed 363 Bond Street Development
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which is commonly associated with manufactured gas plant (MGP) sites.
The free product was also identified as being denser than water. The
report concluded that soil impacted by free product is located in a
heterogeneous lens that is approximately 8 inches thick and that the
liquid phase product appears to be coming onto the site from the canal
and originated from another source as coal tar/creosote was never used
or generated onsite.
4. No exceedances of the SCOs were detected in the samples collected.
Bulkhead Replacement – 400 Carroll Street, Brooklyn, NY letter, dated
25 October 2011, completed by PW Grosser Consulting, Inc.
This letter was prepared and submitted to the Mr. Christos Tsiamis of the
USEPA to propose a remedial alternative for the bulkhead replacement at the
400 Carroll Street site. The remedial alternative was designed to contain
NAPL that was observed in the southern portion of the site at depths ranging
from 25 to 30 feet bgs at the site from entering the Gowanus Canal. The
impervious sheeting would extend from 20 to 35 feet bgs and the joints of
the sheeting would be sealed with Adeka Ultra Seal (P-201) to ensure that
the sheeting functions as an impervious barrier.
Soil Sampling – 400 Carroll Street, dated April 2012, completed by Zeb
Environmental
1. Langan compared the soil analytical data collected by Zeb Environmental to
the NYSDEC Brownfields SCOs. Elevated concentrations of VOCs
(1,2-dichloroethene [cis]), acetone, benzene, ethylbenzene, methylene
chloride, propylbenzene-n, o-xyelene, m-xylene, and m&p-xylene) were
detected above the UUOs in P-9 (3.5 to 5 feet bgs), P-10 (3 to 4 feet bgs),
P-4 (6 to 7 feet bgs), P-5 (3.5 to 5 feet bgs), P-7 (4 to 5 feet bgs), and P-8 (4
to 5 feet and 7 to 7.5 feet bgs). Elevated concentrations of SVOCs
(benzo(a)anthracene, benzo(a)pyrene, benzo(b)fluoranthene, benzo(k)fluoranthene,
chrysene, dibenzo(a,h)anthracene, and indeno(1,2,3-cd)pyrene) were detected
above the UUOs at P-2 (4 to 5 feet bgs), above the Residential RUOs at P-9
(3.5 to 5 feet bgs), P-12 (4 to 5 feet bgs), P-2 (4 to 5 feet bgs), P-4 (3.5 to 5
feet bgs), P-7 (4 to 5 feet bgs), and P-8 (4 to 5 feet bgs), above the Restricted
Residential RUOs at P-9 (3.5 to 5 feet bgs), P-10 (3 to 4 feet bgs), P-12 (4 to
Remedial Investigation Work Plan Proposed 363 Bond Street Development
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5 feet bgs), P-1B (4 to 5 feet bgs), P-2 (4 to 5 feet bgs), P-3 (3.5 to 5 feet
bgs), P-4 (3.5 to 5 feet bgs), P-7 (4 to 5 feet bgs), and P-8 (4 to 5 feet bgs),
above the Restricted Commercial RUOs at P-9 (3.5- to 5-feet bgs), P-2 (4- to
5-feet bgs), and P-3 (3.5 to 5 feet bgs), and above the Restricted Industrial
RUOs at P-9 (3.5 to 5 feet bgs), P-12 (4 to 5 feet bgs), P-3 (3.5 to 5 feet bgs),
P-4 (3.5 to 5 feet bgs), and P-8 (4 to 5 feet bgs).
363 and 365 Bond Street
Draft Limited Phase II Environmental Investigation Report – 363 & 365 Bond
Street, dated September 2012, completed by Langan Engineering
1. A geophysical survey of the property was completed as part of this
investigation to determine if the potential extents of underground piping
associated with the former oil terminal operations and to complete utility
markouts at the proposed test boring locations.
The geophysical survey identified multiple pipes of unknown usage on
the southeast corner of the 400 Carroll Street property; however, no
evidence of piping associated with the former ASTs was encountered.
2. Soil borings confirmed that a layer of historic fill consisting of sand and
silt is present from the surface to between 6 and 11 feet bgs at
363 Bond Street. A clay layer was observed underlying the historic fill in
all borings. Groundwater was generally observed to be between 4.5
and 7.5 feet bgs at 363 Bond Street.
3. Groundwater was measured at approximately 8 feet below sidewalk
elevation. There is a 6 foot fluctuation between high and low tide at the
mouth of Gowanus Bay (entrance to the canal) and it is expected that the
groundwater level is effected by to tidal changes. Based on the results of
previous reports, the groundwater flow direction is towards the canal to the
east.
Remedial Investigation Work Plan Proposed 363 Bond Street Development
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363 Bond Street
1. PID readings above background were observed in all four borings ranging
from 2.6 to 264 ppm. PID readings of 264 ppm were measured at 9 feet
bgs in LSB-1, 67.2 ppm at 10.5 feet bgs in LSB-2, 76.3 ppm at 5.5 feet
bgs in LSB-3, and 76.9 ppm at 2.5 feet bgs in LSB-4. LNAPL was
observed in LSB-1 from 8 to 9 feet and 11 to 12 feet bgs
2. A 1.5-foot thick layer of LNAPL was detected in MW-5.
3. Analytical results detected exceedances of UUOs for the VOCs acetone
and ethylbenzene in the LSB-1(gasoline UST area) location and xylenes at
the LSB-1 and LSB-4 (soil excavation area) locations. No other detections
above UUOs were identified. Several SVOCs were detected above the
SCOs in each of the borings completed as part of this investigation.
Acenapthene, fluorene, 2-methylphenol and phenol were detected above the
UUOs and anthracene, dibenzofuran, fluoranthene, naphthalene,
phenanthrene and pyrene were detected above RUOs in LSB-1 (gasoline
UST area). Benzo(a)anthracene, benzo(a)pyrene, benzo(b)fluoranthene,
benzo(k)fluoranthene, chrysene, dibenzo(a,h)anthracene, indeno(1,2,3,-
c,d)pyrene were detected above RUOs in all of the samples collected as part
of this Phase II investigation. All of the soil samples collected as part of this
portion of the investigation were collected from within the deep vadose zone
and within the saturated zone. Vadose zone samples were collected from a
depth ranging from 6 to 9 feet bgs and saturated zone samples were
collected from depths ranging from 11.5 to 12.5 feet bgs
Benzo(a)anthracene, benzo(a)pyrene, benzo(b)fluoranthene, chrysene,
dibenzo(a,h)anthracene and indeno(1,2,3,-c,d)pyrene were detected above
Restricted Industrial RUOs in the LSB-1 sample. Dibenzo(a,h)anthracene
was detected above the Restricted Industrial RUOs in the LSB-3 sample and
benzo(a)pyrene was detected above the Restricted Industrial RUOs in the
LSB-2 through LSB-4 samples. The sample from LSB-1 was also analyzed for
lead, which was detected above the Restricted Residential RUOs.
4. No exceedances to NYSDEC GWQS for VOCs or SVOCs were detected
in groundwater samples. Anthracene was detected below the GWQS at
the MW-2 location (proposed excavation area).
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5. Tetrachloroethene (4,160 µg/m3 at LSV-1 and 1,010 µg/m3 at LSV-2) and
trichloroethylene (379 µg/m3 at LSV-1 and 2,180 µg/m3 at LSV-2) were
detected in both samples soil vapor samples. There were no additional
exceedances of the NYSDOH and USEPA criteria for any of the other
BTEX or PCE breakdown products 1,1-Dichloroethane 1,2-Dichloroethene
(cis) in either of the samples.
2.4 Data Usability
ELM Phase II ESA Data Usability
The method detection limit (MDL) is the lowest concentration that can be
qualitatively identified by the method being used for analysis. Method
detection limits for VOCs (1,1,1-trichloroethane, 1,1-dichloroethane, 1,1-
dichloroethene, 1,2-dichloroethane, 1,2-dichloroethene, 1,2-dichloroethene, 1,2-
dichloroethene (cis), 1,2-dichloroethene (trans), acetone, benzene, carbon
tetrachloride, chloroform, ethylbenzene, 2-butanone, toluene, methylene chloride,
trichloroethene, tetrachloroethene, vinyl chloride, and total xylenes) were
reported above the UUOs, Residential RUOs, or Restricted Residential RUOs.
Additionally, the method detection limits for SVOCs (1,2-dichlorobenzene,
benzo(b)fluoranthene, benzo(k)fluoranthene, dibenzo(a,h)anthracene, indeno(1,2,3-
cd)pyrene, 2-methylphenol, 4-methylphenol, pentachlorophenol, and phenol)
were reported above the UUOs, Residential RUOs, Restricted Residential RUOs,
Restricted Commercial RUOs, or Restricted Industrial RUOs in several samples.
Method detection limits for metals (cadmium, selenium, and silver) were
reported above the UUOs, Residential RUOs, and Restricted Residential
RUOs were detected in several samples collected at the 400 Carroll Street
site. The method detection limits for pesticides (4-4’-DDT, DDE, aldrin, and
dieldrin) were above the UUOs or Residential RUOs in several samples collected
from the 363 and 365 Bond Street sites. The exceedance of the method
detection limits in the soil samples is likely due to the moisture content of the
soil sample that was collected. As the site has been characterized as being
impacted with both VOC and SVOCs in the areas where elevated detection
limits were noted in the soil samples the elevated MDLs do not affect the
delineation results and the data is usable as provided.
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Langan Phase II Investigation Data Usability
The MDL for the VOCs 1,4-dioxane, acetone, methyl ethyl ketone, methylene
chloride, cis-1,-dichloroethylene and vinyl chloride in soil were reported above
the UUOs. As the MDLs for these compounds were only in exceedance of the
UUOs, it can be concluded that that data is usable as provided.
MDLs were reported in groundwater above GWQS for 1,2-dibromo-3-
chloropropane, 1,4-dioxane, 2,4-dinitrophenol, 4-nitrophenol, hexachlorobenzene,
hexachlorobutadiene, hexachleorcyclopendtadiene and nitrobenzene as part of the
Phase II investigation. The analytical data was reviewed to determine why the
MDLs of certain compounds exceeded the GQS as discussed above. There
were no dilutions applied to any of the groundwater samples so it was
determined that the MDLs reported for the compounds discussed above are
the lowest concentration that the laboratory equipment is capable of
detecting. Based on this information, it can be concluded that that data is
usable as provided.
2.5 Summary of Previous Environmental Investigations
Based on the results identified in the previous sections, the delineation of
soil and groundwater impacts has been completed; however, additional soil
and groundwater investigation activities will be completed to further
characterize the subsurface soil and groundwater conditions and to further
limit the areas of excavation that are proposed. The following section
provides an AOC specific summary of the results of the previous
environmental investigations.
Former ASTs
Review of historic Sanborn Maps identified five large diameter containment
vessels on the 400 Carroll Street property that were presumed to be
associated with the former operation of the site as an oil terminal. The three
western most structures are identified in the ELM Phase II report as the
remnants of secondary containment structures for former ASTs that
continue to a depth of approximately 8 feet below grade and are constructed
of 12 inch reinforced concrete. The subgrade portion of these three
secondary containment structures remains intact and the structures have
been backfilled to grade with sand. The remaining two secondary
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containment vaults for the former ASTs on the southern portion of the
property remain on site.
As part of the ELM Phase II investigation, 12 soil borings and six test pits
were completed at evenly spaced intervals to determine if the ASTs and the
historic use of the property as an oil terminal had impacted the property.
Soil samples were primarily collected from within the shallow overburden fill
material between 3 to 7 feet bgs. Elevated concentrations of PAHs and
metals above NYSDEC UUOs were detected in the shallow vadose zone. In
eight of the soil samples collected, PAHs and metals were detected in
exceedance of the Restricted Industrial RUOs. Based on these results, the
impacts observed within the fill material were consistent with those typically
associated with historic fill.
Elevated concentrations of VOCs (benzene, toluene, and total xylenes) above the
NYSDEC GWQS were detected in groundwater at five of the seven groundwater
samples collected. PAHs were detected above GWQS at two of the locations
(SB-7/TW and SB-11/TW) and total PCBs were detected above GWQS at
SB-7/TW. Dissolved metals (antimony, iron, magnesium, manganese, and
sodium) were detected above the GWQS in all seven of the samples collected.
Petroleum impacts (odors, staining or elevated PID readings) were identified
in all 12 boring locations and in five of the six test pit locations. No LNAPL
was reported in any of the borings or test pits. The petroleum impacts are
further discussed in the following section.
Based on the results of the previous investigations, delineation of soil and
groundwater impacts has been completed and the only data gap that exists
for this AOC is the absence of soil vapor sampling on the 400 Carroll Street
parcel. Collection of soil vapor sampling within this AOC is proposed as
discussed in Section 3.1.
Petroleum Impacted Hotspots
As result of the Phase II investigations completed by ELM, four petroleum
impacted “hotspots” were identified at the Site. Three of these (two of the
three “hotspots” were combined into an area previously designated as AOC-1
and the third as AOC-2) were located on the north central and southeastern
portion of the 400 Carroll Street site. An area previously designated as (AOC-3)
was located in the central portion of the 363 Bond Street site.
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AOC 1 and 2
Soil and groundwater analytical results of this AOC are discussed in the previous
AOC summary. In a RAP submitted to the NYSDEC and NYCDEP in
February 2009 by ELM, three areas of soil stabilization were identified on the
400 Carroll Street property to address impacts of VOCs, SVOCs and PAHs
associated with the fill material and petroleum impacts. Subsequent to the
submission of the RAP by ELM, P.W. Grosser submitted a RAP to the NYSDEC
and NYCDEP in July 2011 that proposed excavation of the “hotspots” to a depth
of 2 feet into groundwater (7 feet bgs). Completion of the excavations was
proposed to extend to the soil which exhibit no evidence of petroleum impacts
and were to be confirmed by post excavation sampling. This RAP was approved
by the NYSDEC in a letter dated 19 July 2011. A copy of this letter is provided in
Appendix C.
A subsequent investigation was completed by ZEB Environmental in April 2012
to further delineate the “hotspot” areas at 400 Carroll Street. As part of the
investigation 13 test pits were completed and 13 soil samples were collected at
depths that ranged from 3 to 8 feet bgs. The results of the investigation
determined that several VOCs were detected above NYSDEC UUOs and that
several SVOCs were detected above the NYSDEC RUOs. Additionally, as result
of this investigation, the northern two “hotspots” were expanded and combined
into one excavation area (AOC-1) and the AOC-2 area was expanded to the
extents of the petroleum impacted material as shown on the Figure 2.
As identified above, soil impacts have been delineated at AOC-1 and AOC-2 in
areas measuring 6,455 and 2,385 square feet, respectively, and extend to the
limits of the clay and depth to groundwater at depths of approximately 7 feet bgs.
The only data gap that exists for these AOCs is the absence of soil vapor
sampling in this area. Additional soil vapor sampling is proposed as discussed
in Section 3.1.
AOC 3
As part of the ELM Phase II investigation for the 363 Bond Street property,
10 soil borings were completed at evenly spaced intervals to determine if
the historic use of the property as an industrial and manufacturing facility had
impacted the site. Five of these borings were completed as groundwater
monitoring wells. Soil samples were primarily collected from within the
shallow overburden fill material (vadose zone) between 1 to 6 feet bgs and
Remedial Investigation Work Plan Proposed 363 Bond Street Development
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below the groundwater table (saturated zone) between 6 to 16 feet bgs.
Elevated concentrations of PAHs and metals above NYSDEC RUOs were
detected in both the shallow vadose zone and the saturated zone. In nine of
the soil samples collected, PAHs and metals were detected in exceedance
of the Restricted Industrial RUOs. Based on these results, the impacts
observed within the fill material were consistent with those typically
associated with historic fill. The VOCs acetone, benzene, ethylbenzene,
methylene chloride, toluene, and total xylenes were detected above the UUOs in
eight of the soil samples collected.
Petroleum impacts (staining, odors, elevated PID readings and LNAPL) were
identified in all 10 boring locations. LNAPL was reported at the SB-1, MW-3
and MW-5 locations. SB-1 and MW-5 were located within the central portion
of the building, and MW-3 is located at the corner of Bond Street and
1st Street outside of the building.
Elevated concentrations of VOCs (benzene, toluene, ethylbenzene, total xylenes,
and vinyl chloride) above the NYSDEC GWQS were detected in groundwater at
MW-4 and MW-5 which are located within the central portion of the property.
SVOCs were detected above GWQS at MW-2 and MW-5. Total and dissolved
metals were detected above GWQS in all four of the samples collected.
Based on these results ELM prepared a RAP dated February 2009 that
identified that the area in the central portion of the 363 Bond Street property
would be excavated to remove the area of free product that was identified
(AOC 3). Soil stabilization in the areas to the east and west of this excavation
area was proposed.
Langan completed additional sampling in the area of AOC-3 (363 Bond Street) to
provide further delineation of petroleum impacted soils in these areas. Test
borings and soil sampling was completed to the north (LSB-3 and LSB-4) and
west (LSB-2) of the extent of impacted soils identified in the RAP. The results
revealed that SVOCs were detected above the RUO for Residential and
Industrial use; however, the exceedances consisted of low concentrations (less
than 10 ppm) of PAH compounds. The presence of these PAHs at these
concentrations is consistent with the presence of historic fill which has been
documented site wide. The presence of LNAPL was noted historically and during
the recent sampling conducted as part of this investigation at MW-5. The
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presence of these impacts may be the result of localized soil impacts, as noted
in the sample collected at the depth of the water table at MW-5 during the 2005
sampling event (which exhibited elevated PAH and naphthalene concentrations
in soil).
Based on the results of the previous investigations that have been completed for
this AOC, additional soil and groundwater delineation to refine the excavation
area extents is proposed as discussed in Section 3.1. Additionally, in order to
assess the presence of LNAPL in the groundwater at the MW-5 location,
additional groundwater monitoring wells will be installed within this AOC.
Gasoline USTs (AOC-5)
The potential presence of two gasoline USTs were identified on the historic
Sanborn maps on the western portion of the 363 Bond Street property within
the footprint of the current building.
As part of the Langan Limited Phase II Investigation, one soil boring (LSB-1) and
one soil vapor sample (LSV-1) were completed directly downgradient of the
former USTs and one additional boring (LSB-2) was completed further
downgradient of the tank area. The soil analytical results revealed marginal
exceedences of the UUOs for ethylbenzene and xylenes in the LSB-1 location
and detections of SVOCs (PAHs and napthalenes) and lead above RUOs.
Additionally, LNAPL was observed in soil boring LSB-1 from 8 to 12 feet bgs.
Samples collected at LSB-2 identified elevated concentrations of PAHs
compounds, which appear to be associated with fill conditions observed in the
area of AOC-3 and not related to the impacts associated with the USTs. Based
on these results impacted soil and groundwater associated with the USTs will be
addressed via excavation and collection of post excavation soil samples to
confirm the extents of impact.
Soil gas sample results from LSV-1 in the vicinity of the former USTs, revealed
that elevated concentrations of chlorinated VOCs (PCE, TCE and chloroform) are
present below the existing building. Based on the absence of these VOCs in soil
and groundwater in this area, the source of these impacts in soil gas is
unknown. In order to better assess the source of the soil vapor impacts
reported, completion of additional soil, soil gas and groundwater sampling is
included in this Phase II Investigation scope as detailed in Section 3.1.
Remedial Investigation Work Plan Proposed 363 Bond Street Development
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It should be noted that the 2006 NYSDOH Final Vapor Intrusion Guidance,
Matrix 2 guidance identifies that sub-slab soil vapor concentrations of PCE
greater than 1,000 ug/m3 require mitigation. As the LSV-1 soil vapor sample
results were greater than 1,000 ug/m3, installation and operation of soil vapor
mitigation system (active or passive) below building in this area will be required
as part of the future redevelopment of the Site, unless remediation is completed
that results in a decrease in these concentrations.
Based on the results of this investigation, impacts to soil and groundwater from
the gasoline USTs have been identified; however, further delineation of these
impacts proposed as discussed in Section 3.1.
EPA Coal Tar Study
The results of the USEPA Remedial Investigation of the Gowanus Canal in
the areas of the site were presented in a January 2011 Gowanus Canal
Remedial Investigation Report. As part of the investigation, coal tar impacts
were identified within the canal adjacent to the 400 Carroll Street site. The
USEPA installed two monitoring wells (MW-36 and MW-43) on the
southeastern portion of the 400 Carroll Street site as part of the June 2010
Remedial Investigation activities. In order to address the potential that
releases of coal tar from the subject property were discharged to the canal, a
geoprobe investigation was completed with USEPA oversight at the
400 Carroll Street site in June 2011 by PW Grosser. As part of the
investigation, eleven soil borings (GP-1 through GP-11) were installed on the
southeastern portion of the site to a depth of 30 feet bgs. Based on the
results of previous investigations completed at the site, this depth
corresponds to the lower aquifer at the site that is separated from the
shallow groundwater aquifer at the site by a clay layer of significant
thickness. The deep geoprobe investigation was completed in the vicinity of
these two monitoring wells to further address the potential for DNAPL at the
site; although DNAPL was not observed in the wells but de minimus
amounts were identified in the core samples during the installation of the
two USEPA monitoring wells. In three of the eleven borings, thin droplets of
NAPL were observed. Soil samples collected as part of this investigation did
not report exceedances of the NYSDEC UUOs. A recoverable quantity of
liquid phase NAPL was not observed in any of the borings; however, soil that
was saturated with NAPL was analyzed for fingerprint analysis. Based on
the results of this analysis the NAPL was determined to be coal tar.
Remedial Investigation Work Plan Proposed 363 Bond Street Development
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In a letter dated September 2012, the USEPA identified that groundwater
monitoring wells were installed on the 400 Carroll Street (MW-36 and
MW-43) property. A copy of the letter is provided in Appendix C. According
to Appendix O of the 2011 USEPA Remedial Investigation Report, MW-36
and MW-43 were installed to a depth of approximately 38 feet bgs, and MW-
5 and MW-6 were installed to a depth of approximately 35 feet bgs
(approximately 30 feet below the water table) to assess the potential of deep
impacts to the canal from the sites. Based on the results of their
investigation and the investigation completed by PW Grosser in 2011, it was
determined that the NAPL impacts identified on the 400 Carroll Street site
were localized and minimal; however, even though the presence of these
impacts may have originated in the canal, the presence of these impacts on
the site has the potential to impact the canal. The contemplated remedial
approach will include a sealed steel bulkhead on the outboard side of the
existing timber bulkhead to isolate these impacts both to and from the canal.
Details of the sheeting design will be provided in a Remedial Action
Workplan for the site.
Based on the results of the previous investigation and the USEPA letter, no
further delineation of the DNAPL impacts are proposed for this AOC.
Historic Fill
Based on the results of shallow soil sampling completed throughout the
three parcels, historic fill material is present above the confining clay layer at
each of the sites. This fill material is impacted by PAHs, SVOCs and metals
at concentrations typical of historic urban fill. As the fill material is located
site wide, further delineation of this material is not proposed. The presence
of fill material will be addressed by development of a Construction Soil
Management Plan and capping associated with redevelopment of the site.
Remedial Investigation Work Plan Proposed 363 Bond Street Development
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3.0 REMEDIAL INVESTIGATION
3.1 Investigation Rationale
Soil, Soil Vapor, and Groundwater
An investigation of soil, soil vapor and groundwater is proposed to delineate
previously identified “hot spots” to allow for the mass excavation of this
material, and to provide further characterization of soil and groundwater at
the Site and comply with OER’s updated practices. The rationale for the
borings, soil vapor locations and groundwater wells is as follows:
Twelve borings will be completed at the Site to address the following AOCs
and to fill in data gaps:
AOC-2: Proposed Excavation Area ‟ 400 Carroll Street, South;
AOC-3: Proposed Excavation Area ‟ 363 Bond Street;
AOC-5: Former UST Area ‟ 363 Bond Street;
A summary of the soil sample locations and sampling rationale is provided in
Table 7. The proposed sampling locations are shown on Figure 9. A total of
10 shallow soil samples (0- to 2 foot bgs interval) will be collected. These
will provide site-wide characterization of the shallow soil at the Site. This is
important due to the proposed slab being between approximately 0.5 to 5.5-
feet above existing grade. This data will be used to augment the previous
investigation soil analytical results that were biased to the soil groundwater
interface.
In addition 12 soil samples will be collected from at the groundwater
interface or locations that exhibit evidence of impact to provide vertical
delineation of selected AOCs.
The following provides the detailed rationale for the collection of all 22 soil
samples, the installation of four additional groundwater monitoring wells, the
collection of 9 groundwater samples and the collection of 25 soil vapor
samples that are proposed as part of this RIWP.
Two samples will be collected from each of the borings LSB-5, LSB-7,
and LSB-10 to address the overall site assessment of soil (for a total of
six samples) at 363 Bond Street. LSB-7 will be completed to assess the
Remedial Investigation Work Plan Proposed 363 Bond Street Development
27
horizontal extent of AOC-5 and LSB-10 will provide southerly delineation
of AOC-2.
Two samples will be collected from each of the borings LSB-9, LSB-21,
LSB-22, and LSB-23, LSB-24, and LSB-27 to complete the delineation of
the hotspot at AOC-3 (for a total of 12 samples). Some of these borings
are within the extent of previous borings where no impacts were
identified (other than historic fill) to determine if the proposed excavation
area can be reduced in size. In addition to horizontal delineation of AOC-3,
borings LSB-21 and LSB-22 will be completed to assess potential impacts
in the area to the south of the former ASTs on 400 Carroll Street.
Two samples will be collected from boring LSB-6 and one sample will be
collected from borings LSB-8 and LSB-25 (for a total of four samples) to
complete vertical and horizontal delineation of previously detected
impacts in the area of the gasoline underground storage tanks (AOC-5)
and define the area to be excavated.
Four soil borings (LSB-21, LSB-22, LSB-25, and LSB-27) will be completed as
monitoring wells (LMW-10, LMW-6, LMW-7, and LMW-9 respectively) to
address the following AOCs:
AOC-2: Proposed Excavation ‟ 400 Carroll Street, North
AOC-3: Proposed Excavation Area ‟ 363 Bond Street
AOC-5: Former UST Area ‟ 363 Bond Street
LMW-6 will be installed on the north side of 363 Bond Street to delineate
impacts from AOC-2 and AOC-3. LMW-7 will be installed in the western end
of the 363 Bond Street parcel to delineate impacts from AOC-5. LMW-9 and
LMW-10 will be installed within the vicinity of the former ASTs address
potential impacts from the former ASTs at 400 Carroll Street. All wells will
be installed to a maximum depth of 15 feet bgs or to a depth that
corresponds to two-feet into the clay layer and with sufficient screen length
to allow the wells to be screened across the groundwater table so that the
potential presence of LNAPL can be assessed.
These wells will also provide better site wide information on groundwater
quality. Additionally, samples will be collected from previously installed wells
as discussed below:
Remedial Investigation Work Plan Proposed 363 Bond Street Development
28
Monitoring wells MW-1, MW-2, MW-3, MW-4, MW-5 will address the overall
site assessment of groundwater at 363 Bond Street.
A total of 25 soil vapor sampling points will be installed throughout the Site.
10 subslab soil vapor samples will be collected from within the building at
363 Bond Street. Ten additional soil vapor samples will be collected at a
depth of five feet bgs (or the depth identified as being approximately 1 foot
above groundwater) at each of the subslab soil vapor sample locations at
363 Bond Street. Five soil vapor sampling points will be installed outside of
the structures at 400 Carroll Street and will be collected at a depth of five
feet bgs or at a depth corresponding to approximately 1 foot above
groundwater.
The soil vapor samples collected from within the building at 363 Bond Street
will consist of samples LSV-3 through LSV-5 and LSV-16 though LSV-22.
One subslab soil vapor sample and one soil vapor sample will be collected
from each point at a depth of five feet bgs or approximately 1 foot above
groundwater. These 20 samples will address the overall site assessment of
soil vapor.
The soil vapor samples collected from outside of the structures located at
400 Carroll Street will consist of LSV-11 through LSV-15. One sample will be
collected from a depth of five feet b.g.s. at each location. These five
samples will be installed to address the overall site assessment of soil vapor.
3.2 Investigation Procedures
Prior to invasive work, a one-call utility mark-out will be completed in accordance
with local laws to locate buried electric, natural gas, telecommunication utilities, etc.
In addition, a private utility mark-out contractor will locate sub-surface utilities
and structures near the proposed test boring locations, so these
investigations can be performed in locations clear of such sub-surface
elements. All soil borings, groundwater monitoring wells and soil vapor points,
with exception of subslab soil vapor samples, will be installed by a qualified
environmental driller. All field activities including the installation of borings,
monitoring wells, soil vapor points as well as the sampling of these media will be
completed by a geologist/engineer under the supervision of a QEP.
Remedial Investigation Work Plan Proposed 363 Bond Street Development
29
Soil Sampling
A qualified environmental driller will advance 19 investigative borings. The on-site
geologist/engineer will screen the soil samples for environmental impacts and
collect environmental samples for laboratory analysis. Site work will comply with
the safety guidelines outlined in the HASP (Appendix D).
The investigative borings will be advanced to the depth of 15 feet below sidewalk
grade using a direct-push drilling method. The proposed boring location plan is
provided on Figure 9. Soil will be collected continuously to the boring termination
depth with a Geoprobe macrocore sampler in two, four- or five-foot increments
using disposable acetate sleeves. Each sample will be screened for organic
vapors with a photo-ionization detector (PID) and evaluated for visual and
olfactory indications of environmental impacts. Soil descriptions will be recorded
in a field log.
A maximum of 10 soil samples will be collected from the zero to two foot below
ground surface (based on the development scenario of a slab on grade
development) and 12 soil samples will be collected from the groundwater interface
or locations that exhibit evidence of impact (an overall total of 22 soil samples).
Samples will not be composite samples but will be discrete grab samples. The
proposed soil sampling rationale is provided in Table 7.
Groundwater Sampling
Groundwater elevation is expected between 1.25 and 7.5 feet below the current
building slab grade at 363 Bond Street and 5- to 10-feet below current grade at
400 Carroll Street. Four soil borings will be converted into permanent
groundwater monitoring wells by inserting 2-inch diameter PVC well screen and
riser into the open borehole. The proper screen size annulus around the well
screen will be filled with clean, appropriately sized silica sand. In silty conditions,
smaller well screen slot size will be used.
In addition to the collection of groundwater samples at locations installed as part
of this RI, groundwater samples will also be collected from existing wells at
363 Bond Street (MW-1, MW-2, MW-3, MW-4, and MW-5). One representative
groundwater sample will be collected from each well by a Langan geologist/
engineer using a peristaltic pump and dedicated Teflon tubing. Sampling will be
conducted in accordance with NYSDEC Draft DER-10 Technical Guidance for
Site Investigation and Remediation, dated December 2002, and Sampling
Remedial Investigation Work Plan Proposed 363 Bond Street Development
30
Guidelines and Protocols, dated March 1991. See Figure 9 for proposed
monitoring well locations.
Soil Vapor Sampling
A total of 10 indoor sub-slab, 10 indoor deep sub-slab, and five exterior soil vapor
samples (for an overall total of 25 samples) will be collected from the proposed soil
vapor locations on the Sample Location Plan (Figure 9). All samples will be collected
in accordance with the Final Guidance for Evaluating Soil Vapor Intrusion in the State
of New York (NYSDOH October 2006). Conditions in the field may require
adjustment to the sampling locations. Groundwater ranges between 1.25 and
10 feet bgs across the subject properties and, as such, the vapor implants will be
set at a depth of 5 feet bgs or at least 1-foot above the capillary fringe.
Sub-slab soil vapor points will be constructed by drilling a 0.5-inch hole
through the slab using a Bosch hammer drill. Teflon-lined polyethylene
tubing will be installed approximately six-inches beneath the slab and sealed
using modeling clay. Deep soil vapor points will be constructed by attached
a soil vapor screen to Teflon-lined polyethylene tubing and lowering the
screen into a borehole to the desired sampling depth. Clean sand will be
used to create a 1-foot sampling interval from the bottom of the 6-inch
screen to the 6-inches above the top of the screen. The sampling interval
will then be sealed by a layer of bentonite clay.
Samples will be collected in Summa canisters which have been certified clean by
the laboratory and analyzed by using USEPA Method TO-15. Flow rate of both
purging and sampling will not exceed 0.2 L/min. Sampling will occur for the duration
of two hours. Note that sampling duration should be a minimum of two hours or
reflect the exposure scenario for sub-slab samples. A sample log sheet will be
maintained summarizing sample identification, date and time of sample collection,
sampling depth, identity of samplers, sampling methods and devices, soil vapor
purge volumes, volume of the soil vapor extracted, vacuum of canisters before and
after the samples are collected, apparent moisture content of the sampling zone,
and chain of custody protocols.
As part of the vapor intrusion evaluation, a tracer gas will be used in accordance
with NYSDOH protocols to serve as a quality assurance/quality control (QA/QC)
device to verify the integrity of the soil vapor probe seal. Helium will be used as the
tracer gas and a bucket will serve to keep it in contact with the probe during testing.
Remedial Investigation Work Plan Proposed 363 Bond Street Development
31
A portable monitoring device will be used to analyze a sample of soil vapor for the
tracer prior to sampling. If the tracer sample results show a significant presence of
the tracer, the probe seals will be adjusted to prevent infiltration. As the conclusion
of the sampling round, tracer monitoring will be performed a second time to confirm
the integrity of the probe seals.
Investigation Derived Waste
All soil cuttings generated during boring and monitoring well installations will be
containerized in a clearly labeled DOT-approved 55-gallon drum for future off-site
disposal.
Development and purge water from developing and sampling monitoring wells will
be containerized in a clearly labeled DOT-approved 55-gallon drum for future off-site
disposal.
Disposable sampling equipment including, spoons, gloves, bags, paper towels, etc.
that came in contact with environmental media will be double bagged and disposed
as municipal trash in a facility trash dumpster as non-hazardous trash.
3.3 Sample Analysis
Soil and groundwater samples will be submitted to a New York State
Department of Health (NYSDOH) Environmental Laboratory Accreditation
Program (ELAP)-certified laboratory for the analysis of:
„ Volatile Organic Compounds by EPA Method 8260;
„ Semi-volatile organic compounds by EPA Method 8270;
„ Pesticides/PCBs by EPA Method 8081/8082; and
„ Target Analyte List metals by EPA Method 6010;
All groundwater samples will be analyzed for both filtered and unfiltered metals.
Soil vapor samples will be analyzed for VOCs by using USEPA Method TO-15.
3.4 Reporting
A Remedial Investigation Report (RIR) will be prepared following completion
of the field activities and receipt of the laboratory data. The Report will be
prepared using the OER template for the Phase II ESI Report and will provide
Remedial Investigation Work Plan Proposed 363 Bond Street Development
32
detailed summaries of the investigative findings and soil and groundwater
analytical results compared to the NYSDEC Part 375-6.8(a) Unrestricted Used
Soil Cleanup Objectives, appropriate Part 375-6.8(b) Restricted Soil Cleanup
Objectives and NYSDEC Part 703 Groundwater Quality Standards (GQS)
(class GA) or Division of Water Technical and Operational Guidance Series
(TOGS) 1.1.1 Ambient Water Quality Standards (AWQS). The Report will
include an updated Site Plan and remedial recommendations, as warranted.
4.0 QUALITY ASSURANCE/QUALITY CONTROL
4.1 Quality Assurance/Quality Control Procedures
QA/QC procedures will be used to provide performance information with regard to
accuracy, precision, sensitivity, representation, completeness, and comparability
associated with the sampling and analysis for this investigation. Field QA/QC
procedures will be used (1) to document that samples are representative of
actual conditions at the Site and (2) identify possible cross-contamination from
field activities or sample transit. Laboratory QA/QC procedures and analyses will
be used to demonstrate whether analytical results have been biased either by
interfering compounds in the sample matrix, or by laboratory techniques that
may have introduced systematic or random errors to the analytical process. A
summary of the field and laboratory QA/QC procedures is provided below.
4.2 Field QA/QC
Field QA/QC will include the following procedures:
„ Calibration of field equipment, including PID, on a daily basis;
„ Analysis of trip blank (VOCs only) and duplicate samples;
„ Use of dedicated and/or disposable field sampling equipment;
„ Proper sample handling and preservation;
„ Proper sample chain of custody documentation; and,
„ Completion of report logs.
The above procedures will be executed as follows:
„ Five duplicate samples (two soil, one groundwater, and two soil vapor), one
soil matrix spike/matrix spike duplicate sample, one groundwater matrix
spike/matrix spike duplicate sample, three field blanks (two soil and one
groundwater), one trip blank (groundwater or methanol preserved soil) per
Remedial Investigation Work Plan Proposed 363 Bond Street Development
33
shipped cooler containing groundwater samples to be analyzed for VOCs,
and one ambient air sample (soil vapor) per day that soil vapor samples are
being collected will be collected to evaluate field sampling precision or
reproducibility of measurements of the same parameter under the given set
of conditions;
„ Disposable sampling equipment, including acetate sleeves, latex gloves, and
disposable bailers (or sample tubing), will be used to minimize cross-
contamination between samples;
„ For each of the parameters analyzed, a sufficient sample volume will be
collected to adhere to the specific analytical protocol, and provide sufficient
sample for reanalysis if necessary;
„ Because plasticizers and other organic compounds inherent in plastic
containers may contaminate samples requiring organic analysis, samples will
be collected in glass containers, with the exception of the nitrate-preserved
groundwater sample for metals analysis;
„ Appropriate sample preservation techniques, including cold temperature
storage at 4º C, will be utilized to ensure that the analytical parameters
concentrations do not change between the time of sample collection and
analysis; and,
„ Samples will be analyzed prior to the expiration of the respective holding
time for each analytical parameter to ensure the integrity of the analytical
results.
4.3 Sample Custody
Sample handling in the field will conform to appropriate sample custody
procedures. Field custody procedures include proper sample identification,
chain-of-custody forms, and packaging and shipping procedures. Sample labels
will be attached to all sampling bottles before field activities begin to ensure
proper sample identification. Each label will identify the site and sample location.
Styrofoam or bubble wrap will be used to absorb shock and prevent breakage of
sample containers. Ice or ice packs will be placed in between the plastic bags for
sample preservation purposes.
After each sample is collected and appropriately identified, the following
information will be entered into the chain-of-custody form:
Remedial Investigation Work Plan Proposed 363 Bond Street Development
34
„ Site name and address;
„ Sampler(s)’ name(s) and signature(s);
„ Names and signatures of persons involved in the chain of possession of
samples;
„ Sample number;
„ Number of containers;
„ Sample location;
„ Date and time of collection;
„ Type of sample, sample matrix and analyses requested;
„ Preservation used (if any); and,
„ Any pertinent field data collected (pH, temperature, conductivity, Dissolved
Oxygen [DO]).
The sampler will sign and date the “Relinquished” blank space prior to removing
one copy of the custody form and sealing the remaining copies of the form in a
Ziploc plastic bag taped to the underside of the sample cooler lid. The sample
cooler will be sealed with tape prior to delivery or shipment to the laboratory.
4.4 Report Logs
Field logs and borings logs will be completed during the course of this
investigation. A field log will be completed on a daily basis which will describe
all field activities including:
„ Project number, name, manager, and address;
„ The date and time;
„ The weather conditions;
„ On-site personnel and associated affiliations;
„ Description of field activities; and,
„ Pertinent sample collection information including sample identification
numbers, description of samples, location of sampling points, number of
samples taken, method of sample collection and any factors that may affect
its quality, time of sample collection, name of collector, and field screening
results.
A boring log will be completed for each boring and will include the following
information:
Remedial Investigation Work Plan Proposed 363 Bond Street Development
35
„ Project number, name, manager, and location;
„ The date and time;
„ Drilling company and method used;
„ Boring number;
„ Total boring depth and water table depths; and,
„ Pertinent soil sample information including sample number, interval, depth,
amount recovered, color, composition, percent moisture, visual and olfactory
observations of contamination, and PID readings.
4.5 Laboratory QA/QC
AN ELAP-certified laboratory will be used for all sample analyses. The laboratory
will follow the following QA/QC protocols. All samples will be delivered to the
laboratory within 24 hours of sample collection. Samples will be received by
laboratory personnel, who will inspect the sample cooler(s) to check the integrity
of the custody seals. The cooler(s) will then be opened, the samples unpackaged,
and the information on the chain-of-custody form examined. If the shipped
samples match those described on the chain-of-custody form, the laboratory
sample custodian will sign and date the form on the next “Received” blank and
assume responsibility for the samples. If problems are noted with the sample
shipment, the laboratory custodian will sign the form and record problems in the
“Remarks” box. The custodian will then immediately notify the Project Manager
so appropriate follow-up steps can be implemented on a timely basis.
A record of the information detailing the handling of a particular sample through
each stage of analysis will be maintained by the laboratory. The record will
include:
„ Job reference, sample matrix, sample number, and date sampled;
„ Date and time received by laboratory, holding conditions, and analytical
parameters;
„ Extraction date, time and extractor’s initials (if applicable), analysis date, time,
and analyst’s initials; and,
„ QA batch number, date reviewed, and reviewer’s initials.
Remedial Investigation Work Plan Proposed 363 Bond Street Development
36
5.0 HEALTH AND SAFETY PLAN (HASP)
5.1 Health and Safety Plan (HASP)
The investigation Health and Safety Plan (HASP) is included in Appendix D. The
Site Safety Officer will be the geologist/engineer responsible for overseeing and
completing investigation activities. Investigative work performed under this
Work Plan will be in full compliance with applicable health and safety laws and
regulations, including Site and OSHA worker safety requirements and
HAZWOPER requirements. Confined space entry, if any, will comply with OSHA
requirements and industry standards and will address potential risks. The parties
performing the investigation work will ensure that performance of work is in
compliance with the HASP and applicable laws and regulations.
All field personnel involved in investigation activities will participate in training
required under 29 CFR 1910.120, including 40-hour hazardous waste operator
training and annual 8-hour refresher training. Site Safety Officer will be
responsible for maintaining workers training records.
Personnel entering any exclusion zone will be trained in the provisions of the
HASP and be required to sign a HASP acknowledgment. Site-specific training
will be provided to field personnel. Additional safety training may be added
depending on the tasks performed. Emergency telephone numbers will be
posted at the site location before any work begins. A safety meeting will be
conducted before each shift begins. Topics to be discussed include task hazards
and protective measures (physical, chemical, environmental); emergency
procedures; PPE levels and other relevant safety topics. Meetings will be
documented in a log book or specific form. Potential on-site chemicals of
concern include VOCs, SVOCs, pesticides/PCBs, and heavy metals. Information
fact sheets for each contaminant group and/or MSDS’ are included in the HASP.
An emergency contact sheet with names and phone numbers for all pertinent
project personnel as well as regulatory hotline information is included in the
HASP. That document will define the specific project contacts for use in case of
emergency.
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2012-11-09, Rev.2013-07-10).doc
Table 1HISTORIC SAMPLING SUMMARY
PROPOSED BOND STREET DEVELOPMENT
Brooklyn, New York
Matrix Sample Location Sample Depth (ft bgs) Analysis Matrix Sample Location Sample Depth (ft bgs) Analysis
SB-1/4-5 4.0'-5.0' MW-1/3-4 7.0'-8.0'
SB-3/5-7 5.0'-7.0' MW-1/9-10 9.0'-10.0'
SB-4/3-5 3.0'-5.0' MW-2/1-3 1.0'-3.0'
SB-6/4-6 4.0'-6.0' MW-2/9-10 9.0'-10.0'
SB-8/5-7 5.0'-7.0' MW-3/4-6 4.0'-6.0'
SB-10/1-3 1.0'-3.0' MW-3/13-15 13.0'-15.0'
SB-11/4-5 4.0'-5.0' MW-4/6-8 6.0'-8.0
SB-12/2-4 2.0'-4.0' MW-4/12-14 12.0'-14.0'
SB-2/9-10 9.0'-10.0' MW-5/7.5-9.5 7.5'-9.5'
SB-5/19-20 19.0'-20.0' MW-5/13-15 13.0'-15.0'
SB-7/14-15 14.0'-15.0' SB-1/1-4 1.0'-4.0'
SB-9/3-5 3.0'-5.0' SB-1/10-12 10.0'-12.0'
SB-11/14-15 14.0'-15.0' SB-2/6-8 6.0'-8.0'
TP-1/0.5-3 0.5'-3.0' SB-2/10-12 10.0'-12.0'
TP-1/3-3.5 3.0'-3.5' SB-3/6-8 6.0'-8.0'
TP-3/4-7 4.0'-7.0' SB-3/10-12 10.0'-12.0'
TP-4/4-5 4.0'-5.0' SB-4/9-10.5 9.0'-10.5'
TP-5/1.5-3 1.5'-3.0' SB-4/14-16 14.0'-16.0'
TP-6/2.7-4.7 2.7'-4.7' SB-5/5-7 5.0'-7.0'
MW-1 --- SB-5/7-8 7.0'-8.0'
SB-2/TW --- MW-1 7.89'
SB-3/TW --- MW-2 5.41'
SB-6/TW --- MW-4 11.66'
SB-7/TW --- MW-5 10.42'
SB-11/TW ---
SB-12/TW ---
Matrix Sample Location Sample Depth (ft bgs) Analysis
GP-02 25.0'-30.0' Matrix Sample Location Sample Depth (ft bgs) Analysis
GP-04 25.0'-30.0' LSB-1 7.5' - 9.5' VOCs, SVOCS, Lead
GP-10 25.0'-30.0' 6.5' - 8.5'
GP-11 25.0'-30.0' 11.5' - 13.5' VOCs
6.0' - 8.0' SVOCs
12.0' - 14.0'
Matrix Sample Location Sample Depth (ft bgs) Analysis LSB-4 7.0' - 9.0'
TP-1 --- MW-2 --- VOCs
TP-3 --- MW-4 --- SVOCs
TP-6 --- LSV-1 subslab
TP-7 --- LSV-2 subslab
TP-8 ---
Composite ---
Groundwater PPW-3 --- VOCs
Matrix Sample Location Sample Depth (ft bgs) Analysis
NE Corner ---
NW Corner ---
SE Corner ---
SW Corner ---
Groundwater W1 --- VOCs
Matrix Sample Location Sample Depth (ft bgs) Analysis
P-9 3.5'-5.0'
P-9 6.5'-7.0'
P-10 3.0'-4.0'
P-10 7.0'-8.0'
P-12 4.0'-5.0'
P-1B 4.0'-5.0'
P-1B 6.0'-7.0'
P-2 4.0'-5.0'
P-2 6.0'-7.0'
P-3 3.5'-5.0'
P-3 7.0'-7.5'
P-4 3.5'-5.0'
P-4 6.0'-7.0'
P-5 3.5'-5.0'
P-5 7.0'-7.5'
P-6 4.0'-4.5'
P-6 6.5'-7.0'
P-7 4.0'-5.0'
P-7 7.0-7.5'
P-8 4.0'-5.0'
P-8 7.0'-7.5'
SoilVOCs
SVOCs
Soil
Soil
Groundwater
Langan Engineering Phase II Due Diligence Sampling Summary
VOCs
SVOCs
PCBs
Metals
VOCs
SVOCs
Groundwater
Soil
VOCs
SVOCs
PCBs
Metals
VOCs
SVOCs
Zeb Environmental
Soil
Groundwater
P.W. Grosser Consulting. Inc / P.W. Grosser Consulting Engineer & Hydrogeologist, PC
SoilVOCs
SVOCs
Soil
VOCs
SVOCs
Pesticides
PCBs
Metals
LSB-2
LSB-3
Tradewinds
Soil
363 BOND STREET
Environmental Liability Management of New York, LLC Phase II Sampling Summary
400 CARROLL STREET
Environmental Liability Management of New York, LLC Phase II Sampling Summary
VOCsSoil Vapor
SoilVOCs
SVOCs
Cosmos Environmental Services
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3:38 PM
TABLE 2SUMMARY OF HISTORICAL SOIL ANALYTICAL RESULTS
PROPOSED BOND STREET DEVELOPMENT
363 Bond Street
Brooklyn, New York
Consultant:
Sample ID: MW-1/3-4 MW-1/9-10 MW-2/1-3 MW-2/9-10 MW-3/4-6 MW-3/13-15 MW-4/6-8 MW-4/12-14 MW-5/7.5-9.5 MW-5/13-15 SB-1/1-4 SB-1/10-12 SB-2/6-8 SB-2/10-12
Laboratory Sample Number: 209324-001 209324-002 209324-003 209324-004 209324-005 209324-006 209324-007 209324-008 209324-009 209324-010 209324-011 209324-012 209324-013 209324-014
Sampling Date: 4/15/2005 4/15/2005 4/15/2005 4/15/2005 4/15/2005 4/15/2005 4/20/2005 4/20/2005 4/20/2005 4/20/2005 4/20/2005 4/20/2005 4/20/2005 4/20/2005
Sampling Depth (ft): 3-4' 9-10' 1-3' 9-10' 4-6' 13-15' 6-8' 12-14' 7.5-9.5' 13-15' 1-4' 10-12' 6-8' 10-12'
VOC Sampling Depth (ft):
Units: (mg/kg) (mg/kg) (mg/kg) (mg/kg) (mg/kg) mg/kg Q mg/kg Q mg/kg Q mg/kg Q mg/kg Q mg/kg Q mg/kg Q mg/kg Q mg/kg Q mg/kg Q mg/kg Q mg/kg Q mg/kg Q mg/kg Q
VOCs
1,1-Dichloroethane 75-34-3 0.27 19 26 240 480 0.0015 U 0.0016 U 0.0017 U 0.0018 U 0.71 U 0.0015 U 0.0018 U 0.0019 U 0.29 U 0.0015 U 0.3 U 0.0016 U 0.0015 U 0.0016 U
1,1-Dichloroethene 75-35-4 0.33 100 100 500 1,000 0.0024 U 0.0024 U 0.0025 U 0.0028 U 0.83 U 0.0024 U 0.0028 U 0.0029 U 0.34 U 0.0022 U 0.35 U 0.0024 U 0.0023 U 0.0025 U
1,2-Dichloroethane 107-06-2 0.02 2.3 3.1 30 60 0.0021 U 0.0022 U 0.0023 U 0.0025 U 0.71 U 0.0021 U 0.0025 U 0.0026 U 0.29 U 0.002 U 0.3 U 0.0022 U 0.0021 U 0.0023 U
1,2-Dichloroethene (cis) 156-59-2 0.25 59 100 500 1,000 0.0014 U 0.0014 U 0.0015 U 0.0017 U 0.71 U 0.0014 U 0.0017 U 0.0018 U 0.29 U 0.042 0.3 U 0.0015 U 0.0014 U 0.0015 U
1,2-Dichloroethene (trans) 156-60-5 0.19 100 100 500 1,000 0.0017 U 0.0017 U 0.0018 U 0.002 U 0.59 U 0.0017 U 0.002 U 0.002 U 0.24 U 0.0016 U 0.25 U 0.0017 U 0.0016 U 0.0018 U
Acetone 67-64-1 0.05 100 100 500 1,000 0.02 B 0.024 B 0.051 B 0.047 B 1.7 U 0.014 0.0024 U 0.0025 U 0.68 U 0.016 0.71 U 0.04 0.002 UB 0.0021 U
Benzene 71-43-2 0.06 2.9 4.8 44 89 0.0017 U 0.0017 U 0.0018 U 0.002 U 0.47 U 0.0017 U 0.011 0.002 U 0.98 J 0.0016 U 0.2 U 0.0017 U 0.0016 U 0.023
Carbon Disulfide 75-15-0 --- --- --- --- --- 0.002 U 0.0058 J 0.0078 0.006 J 1.1 U 0.002 U 0.0024 U 0.0025 U 0.43 U 0.0032 J 0.46 U 0.0021 U 0.002 U 0.0021 U
Carbon tetrachloride 56-23-5 0.76 1.4 2.4 22 44 0.0025 U 0.0025 U 0.0027 U 0.0029 U 1.2 U 0.0025 U 0.003 U 0.0031 U 0.48 U 0.0024 U 0.51 U 0.0025 U 0.0024 U 0.0027 U
Chloroform 67-66-3 0.37 10 49 350 700 0.0013 U 0.0013 U 0.0014 U 0.0015 U 0.83 U 0.0013 U 0.0016 U 0.0016 U 0.34 U 0.0012 U 0.35 U 0.0013 U 0.0013 U 0.0014 U
Ethylbenzene 100-41-4 1 30 41 390 780 0.0021 U 0.0022 U 0.0066 0.0025 U 1.2 U 0.0021 U 0.0025 U 0.0026 U 1.3 J 0.0067 1.9 J 0.0022 U 0.0021 U 0.0038 J
Methyl ethyl ketone (MEK / 2-butanone) 78-93-3 0.12 100 100 500 1,000 0.0027 U 0.0028 U 0.0029 U 0.0032 U 8 B 0.0027 U 0.0033 U 0.0034 U 0.58 U 0.0026 U 0.61 U 0.0037 J 0.0027 U 0.0029 U
Methylene chloride 75-09-2 0.05 51 100 500 1,000 0.006 JB 0.0058 JB 0.0069 JB 0.0074 JB 0.47 UB 0.0066 JB 0.005 UB 0.0059 JB 0.29 JB 0.0089 JB 0.27 JB 0.0073 JB 0.0049 JB 0.0044 UB
Styrene 100-42-5 --- --- --- --- --- 0.0012 U 0.0012 U 0.0016 J 0.0014 U 0.59 U 0.0012 U 0.0014 U 0.0015 U 0.24 U 0.0011 U 0.25 U 0.0012 U 0.0012 U 0.0013 U
Toluene 108-88-3 0.7 100 100 500 1,000 0.002 U 0.002 U 2.9 J 0.0024 U 0.36 U 0.002 U 0.0024 U 0.0025 U 0.67 J 0.0027 J 0.89 J 0.0021 U 0.002 U 0.0085
Trichloroethene 79-01-6 0.47 10 21 200 400 0.002 U 0.002 U 0.0022 U 0.0024 U 0.83 U 0.002 U 0.0024 U 0.0025 U 0.34 U 0.0067 0.35 U 0.0021 U 0.002 U 0.0021 U
Vinyl Chloride 75-01-4 0.02 0.21 0.9 13 27 0.0024 U 0.0024 U 0.0025 U 0.0028 U 0.95 U 0.0024 U 0.0028 U 0.0029 U 0.39 U 0.014 0.41 U 0.0024 U 0.0023 U 0.0025 U
Xylene (total) 1330-20-7 0.26 100 100 500 1,000 0.0054 U 0.0054 U 0.051 0.0063 U 1.2 U 0.0053 U 0.0085 0.0066 U 2.4 J 0.033 3.7 0.0054 U 0.0052 U 0.017
SVOCs
1,2-Dichlorobenzene 95-50-1 1.1 100 100 500 1,000 0.065 U 0.065 U 1.4 U 0.15 U 1.3 U 0.26 U 0.15 U 0.08 U 13 U 0.62 U 2.8 U 0.067 U 0.13 U 0.14 U
2-Methylnaphthalene 91-57-6 --- --- --- --- --- 0.061 U 0.061 U 8.9 2.1 59 16 0.18 J 0.14 J 240 3.2 J 20 0.064 U 0.35 J 0.39 J
4-Chloro-3-methylphenol 35421-08-0 --- --- --- --- --- 0.13 U 0.13 U 2.8 U 0.31 U 2.6 U 0.52 U 0.31 U 0.16 U 26 U 1.3 U ND ND ND ND
Acenaphthene 83-32-9 20 100 100 500 1,000 0.064 U 0.063 U 5.6 J 1.1 1.3 U 0.25 U 0.15 U 0.079 U 200 6.6 19 0.066 U 0.12 U 0.71 J
Acenaphthylene 208-96-8 100 100 100 500 1,000 0.048 U 0.047 U 1.5 J 0.48 J 0.95 U 0.19 U 0.11 U 0.059 U 18 J 1.3 J 8.1 J 0.049 U 0.092 U 0.33 J
Anthracene 120-12-7 100 100 100 500 1,000 0.064 U 0.063 U 11 1.9 1.3 U 0.25 U 0.26 J 0.1 J 270 13 48 0.066 U 0.12 U 0.75 J
Benzo (a) anthracene 56-55-3 1 1 1 5.6 11 0.052 U 0.052 U 26 3.7 1 U 0.21 U 0.48 J 0.19 J 340 16 62 0.056 J 0.25 J 1.9
Benzo (a) pyrene 50-32-8 1 1 1 1 1.1 0.048 U 0.047 U 26 3.7 0.95 U 0.19 U 0.51 J 0.16 J 330 14 61 0.049 U 0.28 J 2.2
Benzo (b) fluoranthene 205-99-2 1 1 1 5.60 11 0.11 U 0.11 U 19 2.8 2.1 U 0.43 U 0.45 J 0.18 J 210 11 38 0.11 U 0.21 U 1.6
Benzo (g,h,i) perylene 191-24-2 100 100 100 500 1,000 0.043 U 0.043 U 18 1.9 0.85 U 0.17 U 0.39 J 0.13 J 200 8.2 31 0.044 U 0.36 J 1.3
Benzo (k) fluoranthene 207-08-9 0.8 1 3.9 56 110 0.043 U 0.043 U 19 2.4 0.85 U 0.17 U 0.21 J 0.16 J 270 10 42 0.045 J 0.13 J 1.3
bis(2-ethylhexyl)phthalate 117-81-7 --- --- --- --- --- 0.051 U 0.051 U 1.1 U 0.12 U 1 U 0.76 J 0.42 J 0.21 J 10 U 0.49 U 2.2 U 0.14 J 0.12 J 0.11 U
Carbozole 86-74-8 --- --- --- --- --- 0.057 U 0.057 U 2.4 J 0.53 J 1.1 U 0.23 U 0.13 U 0.07 U 88 4.1 16 0.059 U 0.11 U 0.46 J
Chrysene 218-01-9 1 1 3.9 56 110 0.049 U 0.048 U 30 4.3 0.97 U 0.2 J 0.58 J 0.27 J 410 18 61 0.064 J 0.3 J 2.2
Dibenzo (a,h) anthracene 53-70-3 0.33 0.33 0.33 0.56 1.1 0.043 U 0.043 U 6.8 J 0.71 J 0.85 U 0.17 U 0.15 J 0.053 U 84 3.9 12 J 0.044 U 0.083 U 0.57 J
Dibenzofuran 132-64-9 --- --- --- --- --- 0.061 U 0.061 U 3.3 J 0.61 J 1.2 U 0.25 U 0.15 U 0.076 U 130 5.3 18 0.064 U 0.12 U 0.6 J
Di-n-butyl phthalate 84-74-2 --- --- --- --- --- 0.051 U 0.051 U 1.1 U 0.12 U 1 U 0.2 U 0.13 J 0.063 U 10 U 0.49 U 2.2 U 0.053 U 0.098 U 0.11 U
Fluoranthene 206-44-0 100 100 100 500 1,000 0.049 U 0.048 U 71 9.1 1.5 J 0.38 J 1.1 0.46 J 950 52 180 0.12 J 0.41 J 3.5
Fluorene 86-73-7 30 100 100 500 1,000 0.05 U 0.05 U 5.6 J 1.3 4.4 J 1.1 J 0.13 J 0.079 J 200 6.8 27 0.052 U 0.096 U 0.85
Indeno (1,2,3-cd) pyrene 193-39-5 0.5 0.5 0.5 5.6 11 0.039 U 0.039 U 15 1.8 0.78 U 0.16 U 0.3 J 0.11 J 170 7.6 27 0.041 U 0.14 J 1.1
Naphthalene 91-20-3 12 100 100 500 1,000 0.066 U 0.066 U 23 2.7 1.3 U 0.26 U 0.26 J 0.17 J 300 5.9 21 0.12 J 0.32 J 1
o-Cresol(s) (2-Methylphenol) 95-48-7 0.33 100 100 500 1,000 0.1 U 0.1 U 2.2 U 0.24 U 2.1 U 0.41 U 0.24 U 0.13 U 20 U 0.99 U 4.4 U 0.11 U 0.2 U 0.22 U
p-Cresol(s) (4-Methylphenol) 106-44-5 0.33 34 100 500 1,000 0.21 U 0.21 U 4.4 U 0.49 U 4.1 U 0.83 U 0.49 U 0.26 U 41 U 2 U 8.8 U 0.22 U 0.4 U 0.56 J
Pentachlorophenol 87-86-5 0.8 2.4 6.7 6.7 55 0.33 U 0.33 U 7.1 U 0.78 U 6.6 U 1.3 U 0.79 U 0.41 U 66 U 3.2 U 14 U 0.35 U 0.64 U 0.73 U
Phenanthrene 85-01-8 100 100 100 500 1,000 0.045 U 0.045 U 45 8.4 6 J 1.7 0.9 J 0.43 J 1,100 49 190 0.14 J 0.18 J 3.1
Phenol 108-95-2 0.33 100 100 500 1,000 0.11 U 0.11 U 2.4 U 0.26 U 2.2 U 0.45 U 0.27 U 0.14 U 22 U 1.1 U 4.8 U 0.12 U 0.22 U 0.24 U
Pyrene 129-00-0 100 100 100 500 1,000 0.053 U 0.053 U 72 7.7 1.2 J 0.4 J 0.77 J 0.39 J 890 45 110 0.13 J 0.38 J 3.1
PCBs/Pesticides
4,4'-DDE 72-55-9 0.0033 1.8 8.9 62 120 0.0005 U 0.00052 U 0.0027 U 0.00061 U 0.0018 J 0.00051 U 0.00061 U 0.37 1.5 0.11 0.0027 U 0.00052 U 0.0027 J 0.00054 U
4,4'-DDT 50-29-3 0.0033 1.7 7.9 47 94 0.00036 U 0.00037 U 0.0019 U 0.00043 U 0.00036 U 0.00036 U 0.00043 U 0.11 0.018 U 0.0017 U 0.0019 U 0.00037 U 0.00035 U 0.00039 U
4,4'-DDD 72-54-8 0.0033 2.6 13 92 180 0.00044 U 0.00045 U 0.0024 U 0.00053 U 0.00045 U 0.00045 U 0.00053 U 0.0055 U 0.023 U 0.0021 U 0.0024 U 0.00045 U 0.00043 U 0.00048 U
Aldrin 309-00-2 0.005 0.019 0.097 0.68 1.4 0.00041 U 0.00042 U 0.0022 U 0.0005 U 0.00042 U 0.00042 U 0.0005 U 0.0052 U 0.021 U 0.002 U 0.0022 U 0.00042 U 0.00041 U 0.00044 U
Alpha-BHC 319-84-6 0.02 0.097 0.48 3.4 6.8 0.00032 U 0.00033 U 0.0017 U 0.00038 U 0.0016 J 0.00032 U 0.00039 U 0.004 U 0.016 U 0.0015 U 0.0017 U 0.00033 U 0.00031 U 0.00034 U
Beta-BHC 319-85-7 0.036 0.072 0.36 3 14 0.00031 U 0.00032 U 0.0017 U 0.0012 J 0.00032 U 0.00032 U 0.00038 U 0.0039 U 0.12 0.013 0.01 J 0.00032 U 0.00031 U 0.00034 U
Chlordane (alpha) 5103-71-9 0.094 0.91 4.2 24 47 0.00013 U 0.00013 U 0.065 0.00015 U 0.00013 U 0.00013 U 0.00015 U 0.0016 U 0.0065 U 0.00061 U 0.00069 U 0.00013 U 0.00013 U 0.00014 U
Delta-BHC 319-86-8 0.04 100 100 500 1,000 0.00012 U 0.00012 U 0.00064 U 0.00014 U 0.00016 J 0.00012 U 0.00014 U 0.0015 U 0.0061 U 0.0043 J 0.0082 J 0.00012 U 0.00012 U 0.00013 U
Dieldrin 60-57-1 0.005 0.039 0.2 1.4 2.8 0.00037 U 0.00038 U 0.053 0.00045 U 0.00038 U 0.00038 U 0.00045 U 0.0047 U 0.019 U 0.0018 U 0.002 U 0.00038 U 0.00037 U 0.0004 U
Endosulfan I 959-98-8 2.4 4.8 24 200 920 0.00017 U 0.00018 U 0.16 0.0002 U 0.00017 U 0.00017 U 0.00021 U 0.0021 U 0.0087 U 0.00082 U 0.00092 U 0.00018 U 0.00017 U 0.00018 U
Endosulfan II 33213-65-9 2.4 4.8 24 200 920 0.0002 U 0.0002 U 0.0011 U 0.00024 U 0.0002 U 0.0002 U 0.00024 U 0.0025 U 0.01 U 0.00094 U 0.011 J 0.0002 U 0.00019 U 0.00021 U
Endosulfan Sulfate 1031-07-8 2.4 4.8 24 200 920 0.0002 U 0.00021 U 0.0011 U 0.031 0.0002 U 0.0002 U 0.0058 0.0025 U 0.01 U 0.00096 U 0.23 0.00021 U 0.0002 U 0.0024 J
Endrin aldehyde 7421-93-4 0.00037 U 0.00038 U 0.028 0.00045 U 0.00038 U 0.00038 U 0.00045 U 0.0047 U 0.019 U 0.0018 U 0.002 U 0.00038 U 0.00037 U 0.0004 U
Endrin ketone 53494-70-5 --- --- --- --- --- 0.00017 U 0.00017 U 0.046 0.0002 U 0.00017 U 0.00017 U 0.0002 U 0.0021 U 0.0085 U 0.0008 U 0.0009 U 0.00017 U 0.00016 U 0.00018 U
Heptachlor 76-44-8 0.042 0.42 2.1 15 29 0.00017 U 0.00018 U 0.00094 U 0.00021 U 0.00018 U 0.00018 U 0.00021 U 0.0022 U 0.035 J 0.00083 U 0.00094 U 0.00018 U 0.00017 U 0.00019 U
Heptachlor epoxide 1024-57-3 --- --- --- --- --- 0.00013 U 0.00014 U 0.015 0.0031 0.0013 J 0.00013 U 0.0014 J 0.0017 U 0.45 0.032 0.068 0.00014 U 0.00013 U 0.0013 J
Lindane 58-89-9 0.1 0.28 1.3 9.2 23 0.00018 U 0.00018 U 0.034 0.00021 U 0.0019 J 0.00018 U 0.00021 U 0.0022 U 0.009 U 0.00084 U 0.00095 U 0.00018 U 0.00017 U 0.00019 U
Methoxychlor 72-43-5 --- --- --- --- --- 0.0025 U 0.0025 U 0.013 U 0.032 0.0025 U 0.0025 U 0.015 J 0.031 U 1.1 0.086 J 0.26 0.0025 U 0.0024 U 0.0026 U
Polychlorinated biphenyls (PCBs) 1336-36-3
Aroclor 1254 11097-69-1 0.1 1 1 1 25 0.0014 U 0.0014 U 0.0015 U 0.0017 U 0.0014 U 0.0014 U 0.0017 U 0.0018 U 0.0014 U 0.0013 U 0.0015 U 0.0014 U 0.0014 U 0.0015 U
Aroclor 1260 11096-82-5 0.1 1 1 1 25 0.0046 U 0.0048 U 0.005 U 0.0056 U 0.0047 U 0.0047 U 0.0056 U 0.008 J 0.0047 U 0.0044 U 0.005 U 0.0048 U 0.0046 U 0.005 U
Metals
Aluminum 7429-90-5 --- --- --- --- --- 10,200 9,900 3,250 4,330 4,500 4,590 4,830 5,170 3,480 1,960 2,780 4,590 749 4,300
Arsenic 7440-38-2 13 16 16 16 16 3.1 B 4.5 J 51.5 13.9 2 J 2.2 J 17 5.1 J 80.3 2.8 J 8.6 J 5.6 J 1.4 U 7.7 J
Barium 7440-39-3 350 350 400 400 10,000 49.6 55.6 524 131 39 40.8 502 128 1,060 28 164 166 30.5 170
Beryllium 7440-41-7 7.2 14 72 590 2,700 0.7 U 0.71 U 0.65 U 0.74 U 0.5 U 0.69 U 0.8 U 0.71 U 0.72 U 0.6 U 0.64 U 0.61 U 0.57 U 0.67 U
Cadmium 7440-43-9 2.5 2.5 4.3 9.3 60 1.4 U 1.4 U 1.3 U 1.5 U 1 U 1.4 U 1.6 U 1.6 J 1.5 J 1.2 U 4.7 1.2 U 3.4 B 1.3 U
Calcium 7440-70-2 --- --- --- --- --- 989 1,360 12,300 20,000 2,020 1,930 6,960 46,700 27,900 15,300 6,780 6,270 671 16,900
Chromium 7440-47-3 1 22 110 400 800 22.2 21.2 11.9 11.4 9.4 9.8 9.4 7.1 14 4.4 12.2 9 2.8 J 6.8
Cobalt 7440-48-4 --- --- --- --- --- 8.6 7.5 5.2 4.3 5.3 4.9 4.8 2.9 2.9 1.7 J 3.8 4.2 1.2 J 4.7
Copper 7440-50-8 50 270 270 270 10,000 26 20.2 354 69.2 11.8 12.7 67.7 23.3 2,680 16.5 76.9 16 46.7 33.3
Iron 7439-89-6 --- --- --- --- --- 19,700 20,200 15,200 9,700 9,150 9,630 6,870 7,470 10,500 3,650 7,210 11,300 2,120 9,950
Lead 7439-92-1 63 400 400 1,000 3,900 12.6 23.6 851 674 41.7 49.2 1,290 201 1,420 37.5 489 106 91.9 1,450
Magnesium 7439-95-4 --- --- --- --- --- 3,010 2,770 3,020 3,290 2,260 2,360 1,170 2,030 2,630 2,450 1,430 1,680 91.7 1,170
Manganese 7439-96-5 1600 2,000 2,000 10,000 10,000 315 264 192 145 353 263 168 144 307 62.6 133 278 14.2 99
Mercury (elemental) 7439-97-6 0.18 0.81 0.81 2.8 5.7 0.041 J 0.042 J 9.9 0.68 0.074 0.11 1.6 0.84 19.5 0.12 1.5 0.11 0.18 0.38
Nickel 7440-02-0 30 140 310 310 10,000 23.3 20.5 25.7 25.2 24.3 22 12.5 9.6 14.1 4.7 J 14 13.9 5.3 J 9.7
Potassium 7440-09-7 --- --- --- --- --- 730 714 614 608 513 562 630 681 457 149 J 488 544 45.5 U 425
Selenium 7782-49-2 3.9 36 180 1,500 6,800 2.2 U 2.3 U 2.1 U 2.4 U 1.6 U 2.2 U 2.5 U 2.3 U 2.3 U 1.9 U 2 U 2 U 5.5 J 2.2 U
Silver 7440-22-4 2 36 180 1,500 6,800 0.45 U 0.46 U 0.42 U 0.47 U 0.32 U 0.44 U 0.51 U 0.45 U 0.65 J 0.38 U 0.41 U 0.39 U 0.36 U 0.43 U
Sodium 7440-23-5 --- --- --- --- --- 144 127 J 430 624 72.3 J 92.5 J 984 677 1,130 417 593 784 34.5 J 392
Vanadium 7440-62-2 --- --- --- --- --- 29.8 28.8 18.3 12.8 13.5 15 23.6 11.8 13.2 5.2 11.8 17.9 5.4 16.9
Zinc 7440-66-6 109 2200 10000 10000 10000 37.5 38.4 552 138 26.2 28.2 483 60.9 1,270 1,050 243 35.8 25.1 57
NOTES:
NYSDEC Soil Cleanup Objective Tables can be found in Tables 375-6.8(a) and 375-6.8(b) dated 14 December 2006.
Italicized results indicate values in which the minimum detection limit (MDL) exceed the criteria.
Sample data were provided in the Phase II Investigation Report, 363 Bond Street by ELM dated May 2005.
--- : No standard indentified
J: Estimated value
U: Indicates that the result is lower than the MDL.
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TABLE 2SUMMARY OF HISTORICAL SOIL ANALYTICAL RESULTS
PROPOSED BOND STREET DEVELOPMENT
363 Bond Street
Brooklyn, New York
Consultant:
Sample ID:
Laboratory Sample Number:
Sampling Date:
Sampling Depth (ft):
VOC Sampling Depth (ft):
Units: (mg/kg) (mg/kg) (mg/kg) (mg/kg) (mg/kg)
VOCs
1,1-Dichloroethane 75-34-3 0.27 19 26 240 480
1,1-Dichloroethene 75-35-4 0.33 100 100 500 1,000
1,2-Dichloroethane 107-06-2 0.02 2.3 3.1 30 60
1,2-Dichloroethene (cis) 156-59-2 0.25 59 100 500 1,000
1,2-Dichloroethene (trans) 156-60-5 0.19 100 100 500 1,000
Acetone 67-64-1 0.05 100 100 500 1,000
Benzene 71-43-2 0.06 2.9 4.8 44 89
Carbon Disulfide 75-15-0 --- --- --- --- ---
Carbon tetrachloride 56-23-5 0.76 1.4 2.4 22 44
Chloroform 67-66-3 0.37 10 49 350 700
Ethylbenzene 100-41-4 1 30 41 390 780
Methyl ethyl ketone (MEK / 2-butanone) 78-93-3 0.12 100 100 500 1,000
Methylene chloride 75-09-2 0.05 51 100 500 1,000
Styrene 100-42-5 --- --- --- --- ---
Toluene 108-88-3 0.7 100 100 500 1,000
Trichloroethene 79-01-6 0.47 10 21 200 400
Vinyl Chloride 75-01-4 0.02 0.21 0.9 13 27
Xylene (total) 1330-20-7 0.26 100 100 500 1,000
SVOCs
1,2-Dichlorobenzene 95-50-1 1.1 100 100 500 1,000
2-Methylnaphthalene 91-57-6 --- --- --- --- ---
4-Chloro-3-methylphenol 35421-08-0 --- --- --- --- ---
Acenaphthene 83-32-9 20 100 100 500 1,000
Acenaphthylene 208-96-8 100 100 100 500 1,000
Anthracene 120-12-7 100 100 100 500 1,000
Benzo (a) anthracene 56-55-3 1 1 1 5.6 11
Benzo (a) pyrene 50-32-8 1 1 1 1 1.1
Benzo (b) fluoranthene 205-99-2 1 1 1 5.60 11
Benzo (g,h,i) perylene 191-24-2 100 100 100 500 1,000
Benzo (k) fluoranthene 207-08-9 0.8 1 3.9 56 110
bis(2-ethylhexyl)phthalate 117-81-7 --- --- --- --- ---
Carbozole 86-74-8 --- --- --- --- ---
Chrysene 218-01-9 1 1 3.9 56 110
Dibenzo (a,h) anthracene 53-70-3 0.33 0.33 0.33 0.56 1.1
Dibenzofuran 132-64-9 --- --- --- --- ---
Di-n-butyl phthalate 84-74-2 --- --- --- --- ---
Fluoranthene 206-44-0 100 100 100 500 1,000
Fluorene 86-73-7 30 100 100 500 1,000
Indeno (1,2,3-cd) pyrene 193-39-5 0.5 0.5 0.5 5.6 11
Naphthalene 91-20-3 12 100 100 500 1,000
o-Cresol(s) (2-Methylphenol) 95-48-7 0.33 100 100 500 1,000
p-Cresol(s) (4-Methylphenol) 106-44-5 0.33 34 100 500 1,000
Pentachlorophenol 87-86-5 0.8 2.4 6.7 6.7 55
Phenanthrene 85-01-8 100 100 100 500 1,000
Phenol 108-95-2 0.33 100 100 500 1,000
Pyrene 129-00-0 100 100 100 500 1,000
PCBs/Pesticides
4,4'-DDE 72-55-9 0.0033 1.8 8.9 62 120
4,4'-DDT 50-29-3 0.0033 1.7 7.9 47 94
4,4'-DDD 72-54-8 0.0033 2.6 13 92 180
Aldrin 309-00-2 0.005 0.019 0.097 0.68 1.4
Alpha-BHC 319-84-6 0.02 0.097 0.48 3.4 6.8
Beta-BHC 319-85-7 0.036 0.072 0.36 3 14
Chlordane (alpha) 5103-71-9 0.094 0.91 4.2 24 47
Delta-BHC 319-86-8 0.04 100 100 500 1,000
Dieldrin 60-57-1 0.005 0.039 0.2 1.4 2.8
Endosulfan I 959-98-8 2.4 4.8 24 200 920
Endosulfan II 33213-65-9 2.4 4.8 24 200 920
Endosulfan Sulfate 1031-07-8 2.4 4.8 24 200 920
Endrin aldehyde 7421-93-4
Endrin ketone 53494-70-5 --- --- --- --- ---
Heptachlor 76-44-8 0.042 0.42 2.1 15 29
Heptachlor epoxide 1024-57-3 --- --- --- --- ---
Lindane 58-89-9 0.1 0.28 1.3 9.2 23
Methoxychlor 72-43-5 --- --- --- --- ---
Polychlorinated biphenyls (PCBs) 1336-36-3
Aroclor 1254 11097-69-1 0.1 1 1 1 25
Aroclor 1260 11096-82-5 0.1 1 1 1 25
Metals
Aluminum 7429-90-5 --- --- --- --- ---
Arsenic 7440-38-2 13 16 16 16 16
Barium 7440-39-3 350 350 400 400 10,000
Beryllium 7440-41-7 7.2 14 72 590 2,700
Cadmium 7440-43-9 2.5 2.5 4.3 9.3 60
Calcium 7440-70-2 --- --- --- --- ---
Chromium 7440-47-3 1 22 110 400 800
Cobalt 7440-48-4 --- --- --- --- ---
Copper 7440-50-8 50 270 270 270 10,000
Iron 7439-89-6 --- --- --- --- ---
Lead 7439-92-1 63 400 400 1,000 3,900
Magnesium 7439-95-4 --- --- --- --- ---
Manganese 7439-96-5 1600 2,000 2,000 10,000 10,000
Mercury (elemental) 7439-97-6 0.18 0.81 0.81 2.8 5.7
Nickel 7440-02-0 30 140 310 310 10,000
Potassium 7440-09-7 --- --- --- --- ---
Selenium 7782-49-2 3.9 36 180 1,500 6,800
Silver 7440-22-4 2 36 180 1,500 6,800
Sodium 7440-23-5 --- --- --- --- ---
Vanadium 7440-62-2 --- --- --- --- ---
Zinc 7440-66-6 109 2200 10000 10000 10000
NOTES:
NYSDEC Soil Cleanup Objective Tables can be found in Tables 375-6.8(a) and 375-6.8(b) dated 14 December 2006.
Italicized results indicate values in which the minimum detection limit (MDL) exceed the criteria.
Sample data were provided in the Phase II Investigation Report, 363 Bond Street by ELM dated May 2005.
--- : No standard indentified
J: Estimated value
U: Indicates that the result is lower than the MDL.
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SUBPART 375-6 (Revised Brownfields) #
CAS No. Unrestricted
Use Residential
SB-3/6-8 SB-3/10-12 SB-4/9-10.5 SB-4/14-16 SB-5/5-7 SB-5/7-8
209324-015 209324-016 209324-017 209324-018 209324-019 209324-020
4/21/2005 4/21/2005 4/21/2005 4/21/2005 4/21/2005 4/21/2005
6-8' 10-12' 9-10.5' 14-16' 5-7' 7-8'
mg/kg Q mg/kg Q mg/kg Q mg/kg Q mg/kg Q mg/kg Q mg/kg Q mg/kg Q mg/kg Q mg/kg Q mg/kg Q mg/kg Q mg/kg Q
0.38 U 0.0015 U 0.34 U 0.0016 U 0.0016 U 0.0015 U < 0.0084 U < 0.00015 U < 0.00015 U < 0.0075 U < 0.0088 U < 0.0076 U < 0.0091 U
0.44 U 0.0024 U 0.4 U 0.0024 U 0.0024 U 0.0023 U < 0.016 U < 0.00028 U < 0.00028 U < 0.014 U < 0.016 U < 0.014 U < 0.017 U
0.38 U 0.0021 U 0.34 U 0.0022 U 0.0022 U 0.0021 U < 0.0083 U < 0.00015 U < 0.00015 U < 0.0074 U < 0.0087 U < 0.0075 U < 0.0090 U
0.38 U 0.0014 U 0.34 U 0.0015 U 0.0015 U 0.0014 U 0.0681 J < 0.00020 U < 0.00020 U 0.0376 J < 0.012 U 0.135 J 0.188 J
0.32 U 0.0017 U 0.28 U 0.0017 U 0.0017 U 0.0016 U < 0.015 U < 0.00026 U < 0.00026 U < 0.013 U < 0.015 U 0.0501 J 0.0622 J
0.88 U 0.042 B 0.8 U 0.018 B 0.018 B 0.016 B 0.217 J 0.0254 0.0357 < 0.093 U < 0.11 U < 0.094 U < 0.11 U
3.1 J 0.0017 U 0.23 U 0.0017 U 0.0017 U 0.0016 U 0.0202 J < 0.00013 U < 0.00013 U < 0.0065 U < 0.0076 U 0.0120 J 0.0360 J
0.57 U 0.002 U 0.51 U 0.0021 U 0.0021 U 0.002 U 0.0357 J < 0.00013 U 0.0013 J < 0.0064 U < 0.0075 U 0.0174 J < 0.0078 U
0.63 U 0.0025 U 0.57 U 0.0026 U 0.0026 U 0.0025 U < 0.0081 U < 0.00014 U < 0.00015 U < 0.0073 U < 0.0085 U < 0.0074 U < 0.0089 U
0.44 U 0.0013 U 0.4 U 0.0013 U 0.0013 U 0.0013 U < 0.0051 U < 0.000089 U < 0.000091 U < 0.0045 U < 0.0053 U < 0.0046 U < 0.0055 U
0.96 J 0.0021 U 1.3 J 0.0022 U 0.0022 U 0.0021 U 2.26 < 0.00028 U < 0.00029 U < 0.014 U < 0.017 U 0.151 0.31
0.76 U 0.012 0.68 U 0.0028 U 0.0028 U 0.0027 U < 0.15 U < 0.0026 U < 0.0026 U < 0.13 U < 0.15 U < 0.13 U < 0.16 U
0.32 JB 0.0055 JB 0.38 JB 0.006 JB 0.0061 JB 0.0042 JB < 0.078 U < 0.0014 U < 0.0014 U < 0.070 U < 0.082 U < 0.071 U < 0.085 U
0.32 U 0.0012 U 0.28 U 0.0012 U 0.0012 U 0.0012 U < 0.0056 U < 0.000099 U < 0.00010 U < 0.0050 U < 0.0059 U < 0.0051 U < 0.0061 U
2.7 J 0.002 U 0.17 U 0.0021 U 0.0021 U 0.002 U 0.0184 J < 0.00011 U < 0.00012 U < 0.0057 U < 0.0067 U 0.0381 J 0.0837
0.44 U 0.002 U 0.4 U 0.0021 U 0.0021 U 0.002 U 0.0605 J < 0.00019 U < 0.00019 U 0.0750 J 0.0211 J < 0.0097 U < 0.012 U
0.51 U 0.0024 U 0.46 U 0.0024 U 0.0024 U 0.0023 U < 0.0088 U < 0.00016 U < 0.00016 U < 0.0079 U < 0.0092 U < 0.0080 U < 0.0096 U
3.9 0.0053 U 5.7 0.0055 U 0.0055 U 0.0053 U NA NA NA NA NA NA NA
1.4 U 0.063 U 0.98 U 0.066 U 0.068 U 0.5 U NA NA NA NA NA NA NA
4.6 J 0.059 U 50 0.2 J 0.064 U 1.1 J 76.2 0.0436 J 0.0427 J 0.343 0.828 1.19 0.176
ND 0.13 U 2 U 0.13 U 0.14 U 1 U < 0.35 U < 0.033 U < 0.034 U < 0.036 U < 0.037 U < 0.037 U < 0.039 U
5.4 J 0.062 U 3 J 0.065 U 0.15 J 2 J 72.2 0.184 0.235 0.759 1.81 0.975 0.291
3.9 J 0.046 U 0.72 U 0.048 U 0.05 U 1.1 J 4.26 0.146 0.121 0.0429 0.355 0.0328 J 0.0286 J
8 0.062 U 5.5 J 0.067 J 0.16 J 4.9 151 0.604 0.740 1.18 3.23 1.49 0.552
22 0.05 U 8.2 0.13 J 0.34 J 11 168 2.67 2.62 1.58 6.45 1.66 0.989
25 0.046 U 7.8 0.13 J 0.34 J 16 152 3.08 2.91 1.41 6.17 1.32 0.902
15 0.1 U 4.8 J 0.12 J 0.28 J 11 150 3.00 2.84 1.49 4.96 1.24 0.754
16 0.041 U 3.5 J 0.092 J 0.26 J 8.4 96.0 2.10 1.91 0.802 3.68 0.731 0.539
18 0.041 U 5.1 J 0.085 J 0.28 J 10 76.7 1.36 1.37 0.722 4.51 0.864 0.619
1.1 U 0.049 U 0.77 U 0.052 U 0.054 U 0.39 U < 0.31 U 0.0356 J 0.0458 J < 0.032 U < 0.033 U < 0.033 U < 0.034 U
1.5 J 0.055 U 2.1 J 0.058 U 0.062 J 0.95 J 57.8 0.110 0.167 0.569 1.10 0.476 0.228
27 0.047 U 7.9 0.16 J 0.41 13 166 2.67 2.58 1.55 6.09 1.58 1.03
4.8 J 0.041 U 1.4 J 0.044 U 0.079 J 3.2 36.9 0.774 0.686 0.300 1.31 0.309 0.201
5.1 J 0.059 U 2.9 J 0.063 U 0.064 U 1.1 J 62.1 0.0904 0.104 0.448 1.17 0.335 0.156
1.1 U 0.049 U 0.77 U 0.052 U 0.054 U 0.39 U < 0.078 U < 0.0074 U < 0.0075 U < 0.0079 U < 0.0082 U < 0.0082 U < 0.0086 U
37 0.047 U 22 0.31 J 0.77 25 473 5.64 5.24 5.03 16.2 4.97 2.48
7.7 J 0.048 U 4.3 J 0.054 J 0.13 J 2.1 J 84.2 0.231 0.260 0.924 2.05 1.11 0.361
12 0.038 U 3.1 J 0.066 J 0.2 J 7.6 89.9 1.91 1.75 0.762 3.55 0.718 0.503
3.9 J 0.064 U 20 0.11 J 0.12 J 2.3 J 102 0.0563 0.0771 0.291 1.04 1.01 0.242
2.2 U 0.1 U 1.6 U 0.11 U 0.11 U 0.79 U 1.50 < 0.038 U < 0.039 U < 0.041 U < 0.042 U < 0.042 U < 0.044 U
4.4 U 0.2 U 3.1 U 0.21 U 0.22 U 1.6 U NA NA NA NA NA NA NA
7 U 0.32 U 5 U 0.34 U 0.35 U 2.6 U < 0.60 U < 0.057 U < 0.058 U < 0.061 U < 0.063 U < 0.063 U < 0.066 U
28 0.044 U 23 0.32 J 0.66 16 539 1.91 2.36 5.37 13.3 6.15 2.29
2.4 U 0.11 U 1.7 U 0.11 U 0.12 U 0.86 U 1.91 < 0.035 U < 0.036 U < 0.037 U < 0.039 U < 0.039 U < 0.041 U
39 0.051 U 16 0.33 J 0.82 21 340 4.30 4.33 3.28 12.1 3.25 2.00
0.075 0.0005 U 0.065 0.0063 0.00052 U 0.0025 U NA NA NA NA NA NA NA
0.0019 U 0.00036 U 0.0017 U 0.00037 U 0.00037 U 0.0018 U NA NA NA NA NA NA NA
0.0024 U 0.00044 U 0.0021 U 0.00046 U 0.00046 U 0.0022 U NA NA NA NA NA NA NA
0.0022 U 0.00041 U 0.017 0.00043 U 0.00043 U 0.0021 U NA NA NA NA NA NA NA
0.0017 U 0.00032 U 0.0016 U 0.00033 U 0.00033 U 0.0016 U NA NA NA NA NA NA NA
0.0017 U 0.00031 U 0.0015 U 0.00033 U 0.00032 U 0.0016 U NA NA NA NA NA NA NA
0.00069 U 0.00013 U 0.00062 U 0.00013 U 0.00013 U 0.00064 U NA NA NA NA NA NA NA
0.00064 U 0.00012 U 0.00058 U 0.00012 U 0.00012 U 0.0006 U NA NA NA NA NA NA NA
0.002 U 0.00037 U 0.0018 U 0.00039 U 0.00039 U 0.0019 U NA NA NA NA NA NA NA
0.00092 U 0.00017 U 0.038 0.00018 U 0.00018 U 0.00086 U NA NA NA NA NA NA NA
0.0011 U 0.0002 U 0.00096 U 0.00021 U 0.00021 U 0.00099 U NA NA NA NA NA NA NA
0.0011 U 0.0002 U 0.00098 U 0.0028 J 0.00021 U 0.001 U NA NA NA NA NA NA NA
0.002 U 0.00037 U 0.0018 U 0.00039 U 0.00039 U 0.0019 U NA NA NA NA NA NA NA
0.0009 U 0.00017 U 0.00081 U 0.00017 U 0.00017 U 0.00084 U NA NA NA NA NA NA NA
0.00094 U 0.00017 U 0.00085 U 0.00018 U 0.00018 U 0.00087 U NA NA NA NA NA NA NA
0.022 0.00013 U 0.00064 U 0.0018 J 0.00014 U 0.019 NA NA NA NA NA NA NA
0.014 0.00018 U 0.0055 J 0.00018 U 0.00018 U 0.00088 U NA NA NA NA NA NA NA
0.091 J 0.0024 U 0.012 U 0.015 J 0.0026 U 0.096 J NA NA NA NA NA NA NA
0.0015 U 0.0014 U 0.88 0.026 0.0015 U 0.0062 J NA NA NA NA NA NA NA
0.005 U 0.0046 U 0.022 U 0.011 J 0.0048 U 0.013 J NA NA NA NA NA NA NA
3,210 8,040 4,060 4,440 9,140 2,800 NA NA NA NA NA NA NA
7 J 7.5 J 2.5 J 2.3 J 5.6 J 39.2 NA NA NA NA NA NA NA
106 69.9 47.4 40 58.1 273 NA NA NA NA NA NA NA
0.68 U 0.65 U 0.54 U 0.68 U 0.6 U 0.58 U NA NA NA NA NA NA NA
1.4 U 1.3 U 32.4 1.4 J 1.2 U 1.2 U NA NA NA NA NA NA NA
6,380 4,650 4,820 2,200 1,200 15,200 NA NA NA NA NA NA NA
8.3 17.1 10.7 9.5 12.8 7.8 NA NA NA NA NA NA NA
4.8 7.3 4.4 6.2 4.3 3.6 NA NA NA NA NA NA NA
78.5 27.9 27.9 14.2 15.4 176 NA NA NA NA NA NA NA
7,080 15,100 9,370 9,930 12,000 9,750 NA NA NA NA NA NA NA
371 41.1 88.5 9.2 J 41 582 435 NA NA NA NA NA NA
1,670 3,730 2,790 2,950 1,950 1,720 NA NA NA NA NA NA NA
136 168 136 165 126 176 NA NA NA NA NA NA NA
0.97 0.048 0.46 0.026 J 0.1 2.4 NA NA NA NA NA NA NA
13.1 46.2 20.5 23.3 12.5 11.2 NA NA NA NA NA NA NA
362 1,290 891 751 372 380 NA NA NA NA NA NA NA
2.2 U 2.1 U 1.7 U 2.2 U 1.9 U 1.9 U NA NA NA NA NA NA NA
0.44 U 0.41 U 0.35 U 0.44 U 0.38 U 0.47 J NA NA NA NA NA NA NA
185 196 566 213 193 269 NA NA NA NA NA NA NA
12.5 19.6 20.7 17 19.4 13 NA NA NA NA NA NA NA
147 136 350 44.9 39.9 520 NA NA NA NA NA NA NA
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\\langan.com\data\EP\data5\100287501\Engineering Data\Environmental\Reports\2012-10 OER Phase II RIWP\Tables\Table 2 - Historical Soil Data for 363 Bond-OVERALL Historic12/6/201212:21 PM
2 of 2
TABLE 3
SUMMARY OF HISTORICAL GROUNDWATER ANALYTICAL RESULTS
PROPOSED BOND STREET DEVELOPMENT
363 Bond Street
Brooklyn, New York
Consultant:
Sample ID: MW�1 MW�2 MW�4 MW�5 MW�2 MW�4
Laboratory Sample Number: 209387!001 209387!002 209387!003 209387!004 JB!15285!3 JB!15285!1 JB!15285!2
Sampling Date: 4/28/2005 4/28/2005 4/28/2005 4/28/2005 8/30/2012 8/30/2012 8/30/2012
Sampling Depth (ft): 7 10 10
Units: (ug/L) ug/l Q ug/l Q ug/l Q ug/l Q ug/l Q ug/l Q ug/l Q
VOCs
1,1,2!Trichloroethane 79!00!5 1 0.6 U 0.6 U 0.6 U 3 U NA NA NA
1,2!Dichloroethane 107!06!2 0.6 0.6 U 0.6 U 0.6 U 3 U < 0.26 U < 0.26 U < 0.26 U
1,2!Dichloroethene (cis) 156!59!2 5 0.6 U 0.6 U 1.5 J 450 < 0.19 U < 0.19 U < 0.19 U
Acetone 67!64!1 5 14 2.4 J 1.4 U 11 J < 3.3 U < 3.3 U < 3.3 U
Benzene 71!43!2 1 0.4 U 0.4 U 1 J 59 < 0.24 U 0.39 J 0.42 J
Bromomethane 74!83!9 5 1.2 U 1.2 U 1.2 U 6 U < 0.22 U < 0.22 U < 0.22 U
Carbon tetrachloride 56!23!5 5 1 U 1 U 1 U 5 U < 0.22 U < 0.22 U < 0.22 U
Ethylbenzene 100!41!4 5 1 U 1 U 1 U 19 J < 0.23 U < 0.23 U < 0.23 U
Methyl ethyl ketone (MEK / 2!butanone) 78!93!3 5 1.2 U 1.2 U 1.2 U 21 J < 2.4 U < 2.4 U < 2.4 U
Methylene chloride 75!09!2 5 0.4 UB 0.4 UB 0.4 UB 2.9 JB < 0.70 U < 0.70 U < 0.70 U
Toluene 108!88!3 5 0.3 U 0.3 U 0.3 U 38 < 0.23 U < 0.23 U 0.24 J
Trichloroethene 79!01!6 5 0.7 U 0.7 U 2.2 J 3.5 U < 0.22 U < 0.22 U < 0.22 U
Vinyl Chloride 75!01!4 2 0.8 U 0.8 U 1.7 J 320 NA NA NA
Xylene (mixed) 1330!20!7 5 1 U 1 U 1 U 94 NA NA NA
SVOCs
1,2,4!Trichlorobenzene 120!82!1 5 0.6 U 0.6 U 0.7 U 7 U NA NA NA
2!Chlorophenol 95!57!8 5* 1 U 1 U 1 U 12 U < 1 U < 1.0 U < 0.99 U
2!Methylnaphthalene 91!57!6 5* 0.6 U 6 C 0.7 U 150 < 0.4 U < 0.40 U < 0.39 U
2!Nitroaniline 88!74!4 5* 1 U 1 U 1 U 10 U < 1.2 U < 1.2 U < 1.1 U
2!Nitrophenol 88!75!5 5* 1 U 1 U 1 U 13 U < 1.6 U < 1.6 U < 1.5 U
2,4!Dichlorophenol 120!83!2 5* 1 U 1 U 1 U 11 U < 1.2 U < 1.2 U < 1.2 U
2,4!Dimethylphenol 105!67!9 5* 0.9 U 0.9 U 0.9 U 260 < 1.6 U < 1.6 U < 1.6 U
2,4!Dinitrophenol 51!28!5 5* 2 U 2 U 2 U 20 U < 17 U < 17 U < 17 U
2,4!Dinitrotoluene 121!14!2 5 1 U 1 U 1 U 11 U < 0.44 U < 0.44 U < 0.43 U
2,4,5!Trichlorophenol 95!95!4 5* 1 U 1 U 1 U 10 U < 1.6 U < 1.6 U < 1.6 U
2,6!Dinitrotoluene 606!20!2 5 0.6 U 0.6 U 0.7 U 7 U < 0.48 U < 0.48 U < 0.47 U
3!Nitroaniline 99!09!2 5* 0.7 U 0.7 U 0.8 U 8 U < 1.3 U < 1.3 U < 1.3 U
3,3'!Dichlorobenzidine 91!94!1 5 0.7 U 0.7 U 0.8 U 8 U < 0.38 U < 0.37 U < 0.37 U
4!Chloroaniline 106!47!8 5 0.6 U 0.6 U 0.7 U 7 U < 0.55 U < 0.55 U < 0.54 U
4!Chloro!3!methylphenol 35421!08!0 5* 1 U 1 U 2 U 16 U < 1.9 U < 1.9 U < 1.9 U
4!Nitroaniline 100!01!6 5* 0.9 U 0.9 U 0.9 U 9 U < 1.7 U < 1.7 U < 1.7 U
4!Nitrophenol 100!02!7 5* 0.9 U 0.9 U 0.9 U 9 U < 5.4 U < 5.4 U < 5.3 U
Acenaphthene 83!32!9 20 0.7 U 7 J 0.8 U 90 J 3.4 U < 0.27 U < 0.27 U
Acenaphthylene 208!96!8 5* 0.7 U 0.7 U 0.8 U 8 U < 0.24 U < 0.24 U < 0.23 U
Anthracene 120!12!7 5* 0.9 U 2 J 0.9 U 20 J 1.2 U < 0.30 U < 0.29 U
Benzo(a)anthracene 56!55!3 5* 0.4 U 0.4 U 0.5 U 10 J < 0.24 U < 0.23 U < 0.23 U
Benzo(a)pyrene 50!32!8 !!! 0.5 U 0.5 U 0.6 U 8 J < 0.24 U < 0.23 U < 0.23 U
Benzo(b)fluoranthene 205!99!2 5* 1 U 1 U 1 U 11 U < 0.48 U < 0.47 U < 0.47 U
Benzo(g,h,i)perylene 191!24!2 5* 0.6 U 0.6 U 0.7 U 7 U < 0.34 U < 0.33 U < 0.33 U
Benzo(k)fluoranthene 207!08!9 5* 2 U 2 U 2 U 18 U < 0.53 U < 0.53 U < 0.52 U
bis(2!Chloroethyl)ether 111!44!4 5 0.5 U 0.5 U 0.6 U 6 U < 0.32 U < 0.32 U < 0.31 U
bis(2!Ethylhexyl)phthalate 117!81!7 5* 3 U 3 U 3 U 28 U < 0.61 U < 0.61 U < 0.6 U
Butyl benzyl phthalate 85!68!7 5* 0.6 U 0.6 U 0.7 U 7 U < 0.3 U < 0.30 U < 0.29 U
Carbazole 0.3 U 5 J 0.3 U 89 J < 0.38 U < 0.37 U < 0.37 U
Chrysene 218!01!9 5* 0.5 U 0.5 U 0.6 U 11 J < 0.3 U < 0.30 U < 0.29 U
Dibenzo(a,h)anthracene 53!70!3 5* 0.9 U 0.9 U 0.9 U 9 U < 0.39 U < 0.39 U < 0.39 U
Dibenzofuran 132!64!9 7 x 10!7
0.9 U 3 J 0.9 U 53 J < 0.28 U < 0.27 U < 0.27 U
Diethyl phthalate 84!66!2 5* 0.9 U 0.9 U 0.9 U 9 U < 0.34 U < 0.34 U < 0.33 U
Dimethyl phthalate 131!11!3 5* 0.6 U 0.6 U 0.7 U 7 U < 0.29 U < 0.29 U < 0.29 U
Di!n!octyl phthalate 117!84!0 5* 0.7 U 0.7 U 0.8 U 8 U < 0.32 U < 0.32 U < 0.31 U
Fluoranthene 206!44!0 5* 0.6 U 2 J 0.7 J 42 J 2 U < 0.33 U < 0.32 U
Fluorene 86!73!7 5* 0.7 U 6 J 0.8 U 59 J 2.7 U < 0.29 U < 0.28 U
Hexachlorobenzene 118!74!1 0.04 0.7 U 0.7 U 0.8 U 8 U < 0.35 U < 0.35 U < 0.34 U
Hexachlorobutadiene 87!68!3 0.5 1 U 1 U 1 U 12 U < 0.53 U < 0.53 U < 0.52 U
Hexachlorocyclopentadiene 77!47!4 5 6 U 6 U 7 U 64 U < 7.4 U < 7.4 U < 7.3 U
Hexachloroethane 67!72!1 5 1 U 1 U 1 U 10 U < 0.57 U < 0.57 U < 0.56 U
Indeno(1,2,3!cd)pyrene 193!39!5 5* 0.7 U 0.7 U 0.8 U 8 U < 0.39 U < 0.39 U < 0.38 U
Isophorone 78!59!1 5* 0.6 U 0.6 U 0.7 U 7 U < 0.28 U < 0.28 U < 0.28 U
Naphthalene 91!20!3 5* 0.7 U 23 0.8 J 620 < 0.27 U < 0.27 U < 0.26 U
Nitrobenzene 98!95!3 0.4 0.5 U 0.5 U 0.6 U 6 U < 0.44 U < 0.43 U < 0.43 U
o!Cresol(s) (2!Methylphenol) 95!48!7 5* 1 U 1 U 1 U 47 J < 1.1 U < 1.0 U < 1.1 U
p!Cresol(s) (4!Methylphenol) 106!44!5 5* 2 U 2 U 2 U 29 J NA NA NA
Pentachlorophenol 87!86!5 5* 2 U 2 U 2 U 18 U < 1.4 U < 1.4 U < 1.4 U
Phenanthrene 85!01!8 5* 0.5 U 10 J 0.6 J 110 J 3.5 U < 0.30 U < 0.3 U
Phenol 108!95!2 5* 0.5 U 0.5 U 0.6 U 7 J < 1.3 U < 1.3 U < 1.3 U
Pyrene 129!00!0 5* 0.4 U 2 J 0.6 J 37 J 1.5 U < 0.28 U < 0.28 U
Environmental Liability Management of New York, LLC
MW�4 (MS/MSD)
Langan Engineering
Ground Water
Quality Standards
Part 703***CAS No.
\\Langan.com\data\EP\data5\100287501\Engineering Data\Environmental\Reports\2012!10 OER Phase II RIWP\Tables\Table 3 ! Historical GW Data for 363 Bond!OVERALL Historic
10/25/20124:11 PM
1 of 2
TABLE 3
SUMMARY OF HISTORICAL GROUNDWATER ANALYTICAL RESULTS
PROPOSED BOND STREET DEVELOPMENT
363 Bond Street
Brooklyn, New York
Consultant:
Sample ID: MW�1 MW�2 MW�4 MW�5 MW�2 MW�4
Laboratory Sample Number: 209387!001 209387!002 209387!003 209387!004 JB!15285!3 JB!15285!1 JB!15285!2
Sampling Date: 4/28/2005 4/28/2005 4/28/2005 4/28/2005 8/30/2012 8/30/2012 8/30/2012
Sampling Depth (ft): 7 10 10
Units: (ug/L) ug/l Q ug/l Q ug/l Q ug/l Q ug/l Q ug/l Q ug/l Q
Environmental Liability Management of New York, LLC
MW�4 (MS/MSD)
Langan Engineering
Ground Water
Quality Standards
Part 703***CAS No.
Pesticides
4,4'!DDE 72!55!9 0.2 0.01 U 0.0098 U 0.0096 U 0.22 NA NA NA
Aldrin 309!00!2 !!! 0.0067 U 0.0064 U 0.0063 U 0.049 J NA NA NA
Beta!BHC 319!85!7 0.04 0.015 U 0.014 U 0.014 U 0.13 NA NA NA
Dieldrin 60!57!1 0.001 0.0066 U 0.0063 U 0.0062 U 0.0067 U NA NA NA
Endosulfan Sulfate 1031!07!8 5* 0.016 U 0.016 U 0.015 U 0.076 J NA NA NA
Heptachlor epoxide 1024!57!3 0.03 0.0066 U 0.0063 U 0.0062 U 0.58 NA NA NA
Toxaphene 8001!35!2 0.06 0.25 U 0.24 U 0.23 U 0.25 U NA NA NA
Polychlorinated biphenyls (PCBs) 1336!36!3 0.09 0.12 U 0.12 U 0.12 U 0.12 U NA NA NA
Aroclor 1221 11104!28!2 0.09 0.12 U 0.12 U 0.12 U 0.12 U NA NA NA
Aroclor 1232 11141!16!5 0.09 0.094 U 0.09 U 0.088 U 0.095 U NA NA NA
Aroclor 1254 11097!69!1 0.09 0.11 U 0.1 U 0.1 U 0.11 U NA NA NA
Aroclor 1260 11096!82!5 0.09 0.095 U 0.091 U 0.089 U 0.096 U NA NA NA
Total Metals
Aluminum 7429!90!5 !!! 97.7 J 92 U 92 U 924 NA NA NA
Antimony 7440!36!0 3 5.4 U 5.4 U 5.4 U 5.4 U NA NA NA
Arsenic 7440!38!2 25 3.9 U 10 J 3.9 U 35.7 J NA NA NA
Barium 7440!39!3 1,000 145 224 21.9 157 NA NA NA
Cadmium 7440!43!9 5 1.1 U 1.1 U 16.4 1.7 J NA NA NA
Calcium 7440!70!2 !!! 87,900 108,000 70,300 28,300 NA NA NA
Chromium 1.3 U 1.3 U 1.3 U 21.2 NA NA NA
Cobalt 7440!48!4 5* 1.8 U 2.1 J 1.8 U 7.1 J NA NA NA
Copper 7440!50!8 200 4.3 U 4.3 U 8.3 J 17.2 NA NA NA
Iron 7439!89!6 300 5,990 3,730 270 3,600 NA NA NA
Iron and Manganese 7493!89!6/7439!96!5 500 6,946 4,274 330 3,771 NA NA NA
Lead 7439!92!1 25 3 U 3.6 J 3 U 227 NA NA NA
Magnesium 7439!95!4 !!! 10,600 32,800 5,800 23,500 NA NA NA
Manganese 7439!96!5 300 956 544 60 171 NA NA NA
Mercury (elemental) 7439!97!6 0.7 0.07 U 0.07 U 0.07 U 0.49 NA NA NA
Nickel 7440!02!0 100 1.9 U 4.1 J 3.7 J 43.2 NA NA NA
Potassium 7440!09!7 !!! 14,000 50,300 6,550 79,100 NA NA NA
Sodium 7440!23!5 20,000 105,000 155,000 28,400 187,000 NA NA NA
Thallium 7440!28!0 5* 10 U 10 U 10 U 10 U NA NA NA
Vanadium 7440!62!2 5* 1.5 U 1.5 U 5.7 J 19.8 NA NA NA
Zinc 7440!66!6 66** 11 U 11 U 27 J 165 NA NA NA
Dissolved Metals
Antimony 7440!36!0 3 5.4 U 5.4 U 5.4 U 5.4 U NA NA NA
Arsenic 7440!38!2 25 3.9 U 7.5 J 3.9 U 30.5 J NA NA NA
Barium 7440!39!3 1,000 110 158 20.9 123 NA NA NA
Cadmium 7440!43!9 5 1.1 U 1.1 U 15.3 1.1 U NA NA NA
Calcium 7440!70!2 !!! 91,400 107,000 73,100 27,600 NA NA NA
Chromium 1.3 U 1.3 U 1.3 U 16.5 NA NA NA
Cobalt 7440!48!4 5* 1.8 U 2.4 J 1.8 U 6.5 J NA NA NA
Copper 7440!50!8 200 4.3 U 4.3 U 5.1 J 6.2 J NA NA NA
Iron 7439!89!6 300 1,290 54 U 70.9 J 1,830 NA NA NA
Iron and Manganese 7493!89!6/7439!96!5 500 2,267 512 132.1 1,982 NA NA NA
Lead 7439!92!1 25 3 U 3 U 3 U 135 NA NA NA
Magnesium 7439!95!4 !!! 11,200 32,200 5970 23,200 NA NA NA
Manganese 7439!96!5 300 977 512 61.2 152 NA NA NA
Nickel 7440!02!0 100 1.9 U 4.6 J 3.9 J 41.9 NA NA NA
Potassium 7440!09!7 !!! 15100 50,400 6690 80,300 NA NA NA
Sodium 7440!23!5 20,000 111,000 156,000 29,000 184,000 NA NA NA
Thallium 7440!28!0 5* 10 U 10 U 10 U 10 U NA NA NA
Vanadium 7440!62!2 5* 1.5 U 1.5 U 5.2 J 17.1 NA NA NA
Zinc 7440!66!6 66** 11 U 11 U 34.9 J 62.9 NA NA NA
NOTES:
* : No criteria established, value is generic criteria
Sample data were provided in the Phase II Investigation Report, 363 Bond Street by ELM dated May 2005.
Italicized results indicate values in which the minimum detection limit (MDL) exceed the criteria.
J: Estimated value
U: Indicates that the result is lower than the MDL.
NYSDEC Groundwater Criteria are a combination of values from Part 703 if the NYS Code and TAGM 4046. Most values are
generic screening values, however where contaminant specific criteria have been established they are used in this table.
\\Langan.com\data\EP\data5\100287501\Engineering Data\Environmental\Reports\2012!10 OER Phase II RIWP\Tables\Table 3 ! Historical GW Data for 363 Bond!OVERALL Historic
10/25/20124:11 PM
2 of 2
Table 4363 Bond Street
Historic Vapor Analytical Results
Proposed Bond Street Development
Brooklyn, New York
Location ID
Sample ID
Lab ID
Sample Date 90th Percentile
Compound CAS No. µg/m3
µg/m3
Result (ug/m3) Q Result (ug/m
3) Q
VOCs
1,1'DICHLOROETHANE 75'34'3 ''' ''' < 0.45 U < 0.45 U
1,1'DICHLOROETHENE 75'35'4 ''' ''' < 0.71 U < 0.71 U
BENZENE 71'43'2 13 9.4 3.2 1.9 J
ETHYLBENZENE 100'41'4 6.4 5.7 < 0.52 U 3.4 J
TETRACHLOROETHYLENE(PCE) 127'18'4 2.5 to 100 * 15.9 to 100 * 4160 1010
TOLUENE 108'88'3 57 43 4.5 8.7
TRICHLOROETHYLENE (TCE) 79'01'6 0.5 to 5 * 4.2 379 2180
O'XYLENE (1,2'DIMETHYLBENZENE) 95'47'6 7.1 7.9 1.7 J 4.8
M AND P XYLENES 179601'23'1 11 22.2 4.3 7.4
NOTES:
1: NYSDOH 2003: Study of Volatile Organic Chemicals in Air of Fuel Oil Heated Homes (Upper Fence criteria)
2: USEPA 2001: Building Assessment and Survey Evaluation (BASE) Database using Summa Cannister Method
* Upper range based on NYSDOH Air Guideline Values as published in the NYSDOH Soil Vapor Intrusion Guidance dated October 2006
October 2006.
''': Not included in study
U: Indicates that the result is lower than the MDL.
J: Estimated Value
8/30/2012
LSV'2
034
JB15244'3
8/30/2012
NYSDOH 1
USEPA 2001 2
LSV'1
033
JB15244'2
TABLE 5HISTORICAL SOIL ANALYTICAL RESULTS
Proposed Bond Street Development
400 Carroll Street
Brooklyn, New York
Consultant:
Sample ID: SUBPART 375#6 (Revised Brownfields) SB�1/4�5 SB�2/9�10 SB�3/5�7 SB�4/3�5 SB�5/19�20 SB�6/4�6 SB�7/14�15 SB�8/5�7 SB�9/3�5 SB�10/1�3 SB�11/4�5 SB�11/14�15 SB�12/2�4 TP�1/0.5�3
Laboratory Sample Number: 207935�001 207935�002 207935�003 207935�004 207935�005 207935�006 207935�007 207935�008 207935�009 207935�010 207935�012 207935�011 207936�005 207935�019
Sampling Date: Unrestricted # Restricted # Restricted # Restricted # 10/25/2004 10/25/2004 10/25/2004 10/25/2004 10/25/2004 10/25/2004 10/25/2004 10/25/2004 10/25/2004 10/25/2004 10/25/2004 10/25/2004 10/25/2004 10/27/2004
Sampling Depth (ft): Residential Residential Commercial Industrial 4�5 9�10 5�7 3�5 19�20 4�6 14�15 5�7 Q 3�5 1�3 4�5 14�15 2�4 0.5�3
Units: (mg/kg) (mg/kg) (mg/kg) (mg/kg) (mg/kg) mg/kg Q mg/kg Q mg/kg Q mg/kg Q mg/kg Q mg/kg Q mg/kg Q mg/kg mg/kg Q mg/kg Q mg/kg Q mg/kg Q mg/kg Q mg/kg Q
VOCs
1,1,1�Trichloroethane 71�55�6 0.68 100 100 500 1,000 0.67 U 0.0087 U 0.69 U 0.62 U 0.0064 U 0.62 U 0.0087 U 3.2 U 0.031 U 0.62 U 3.4 U 0.0089 U 0.00058 U 0.65 U1,1�Dichloroethane 75�34�3 0.27 19 26 240 480 0.67 U 0.0087 U 0.69 U 0.62 U 0.0064 U 0.62 U 0.0087 U 3.2 U 0.031 U 0.62 U 3.4 U 0.0089 U 0.00047 U 0.65 U
1,1�Dichloroethene 75�35�4 0.33 100 100 500 1,000 0.67 U 0.0087 U 0.69 U 0.62 U 0.0064 U 0.62 U 0.0087 U 3.2 U 0.031 U 0.62 U 3.4 U 0.0089 U 0.00047 U 0.65 U
1,2�Dichloroethane 107�06�2 0.02 2.3 3.1 30 60 0.67 U 0.0087 U 0.69 U 0.62 U 0.0064 U 0.62 U 0.0087 U 3.2 U 0.031 U 0.62 U 3.4 U 0.0089 U 0.00058 U 0.65 U
1,2�Dichloroethene (cis) 156�59�2 0.25 59 100 500 1,000 0.67 U 0.0087 U 0.69 U 0.62 U 0.0064 U 0.62 U 0.0087 U 3.2 U 0.031 U 0.62 U 3.4 U 0.0089 U 0.00035 U 0.65 U
1,2�Dichloroethene (trans) 156�60�5 0.19 100 100 500 1,000 0.67 U 0.0087 U 0.69 U 0.62 U 0.0064 U 0.62 U 0.0087 U 3.2 U 0.031 U 0.62 U 3.4 U 0.0089 U 0.0007 U 0.65 U
1,2,3�Trichlorobenzene 87�61�6 ��� ��� ��� ��� ��� NA NA NA NA NA NA NA NA NA NA NA NA NA NA
1,2,3�Trichloropropane 96�18�4 ��� ��� ��� ��� ��� NA NA NA NA NA NA NA NA NA NA NA NA NA NA1,2,4�Trichlorobenzene 120�82�1 ��� ��� ��� ��� ��� NA NA NA NA NA NA NA NA NA NA NA NA NA NA1,2,4�Trimethylbenzene 95�63�6 3.6 47 52 190 380 NA NA NA NA NA NA NA NA NA NA NA NA NA NA
1,3,5�Trimethylbenzene 108�67�8 8.4 47 52 190 380 NA NA NA NA NA NA NA NA NA NA NA NA NA NA
4�Isopropyltoluene 99�87�6 ��� ��� ��� ��� ��� NA NA NA NA NA NA NA NA NA NA NA NA NA NA
Acetone 67�64�1 0.05 100 100 500 1,000 1.7 U 0.048 1.1 J 3.6 0.015 1.2 J 0.016 J 7.9 U 0.14 1.5 U 8.5 U 0.025 0.045 0.82 J
Benzene 71�43�2 0.06 2.9 4.8 44 89 0.086 J 0.0087 U 0.13 J 0.11 J 0.0064 U 0.62 U 0.0087 U 0.63 J 0.031 U 0.62 U 3.4 U 0.0089 U 0.0035 J 0.65 U
n�Butylbenzene 104�51�8 12 100 100 500 1,000 NA NA NA NA NA NA NA NA NA NA NA NA NA NA
Carbon Disulfide 75�15�0 ��� ��� ��� ��� ��� 0.072 J 0.017 0.31 J 0.620 U 0.0064 U 0.62 U 0.019 3.2 U 0.0075 J 0.62 U 3.4 U 0.01 0.0031 J 0.65 U
Carbon tetrachloride 56�23�5 0.76 1.4 2.4 22 44 0.67 U 0.0087 U 0.69 U 0.620 U 0.0064 U 0.62 U 0.0087 U 3.2 U 0.031 U 0.62 U 3.4 U 0.0089 U 0.00035 U 0.65 U
Chlorobenzene 108�90�7 1.1 100 100 500 1,000 0.67 U 0.0087 U 0.69 U 0.620 U 0.0064 U 0.62 U 0.0087 U 3.2 U 0.031 U 0.62 U 3.4 U 0.0089 U 0.00047 U 0.65 U
Chloroform 67�66�3 0.37 10.00 49 350 700 0.67 U 0.0087 U 0.69 U 0.62 U 0.0064 U 0.62 U 0.0087 U 3.2 U 0.031 U 0.62 U 3.4 U 0.0089 U 0.0007 U 0.65 U
Diethylbenzene�p 105�05�5 ��� ��� ��� ��� ��� NA NA NA NA NA NA NA NA NA NA NA NA NA NA
Ethylbenzene 100�41�4 1 30 41 390 780 8.1 0.0029 J 0.077 J 0.11 J 0.0019 J 0.62 U 0.0087 U 3.2 U 0.073 0.62 U 3.4 U 0.0089 U 0.059 0.65 U
p�Ethyltoluene 622�96�8 ��� ��� ��� ��� ��� NA NA NA NA NA NA NA NA NA NA NA NA NA NA
Isopropyl Benzene 98�82�8 ��� ��� ��� ��� ��� NA NA NA NA NA NA NA NA NA NA NA NA NA NAp�Isopropyltoluene 99�87�6 ��� ��� ��� ��� ��� NA NA NA NA NA NA NA NA NA NA NA NA NA NA
Methyl ethyl ketone (MEK / 2�butanone) 78�93�3 0.12 100 100 500 1,000 0.67 U 0.017 U 0.69 U 0.62 U 0.013 U 0.62 U 0.017 U 3.2 U 0.062 U 0.62 U 3.4 U 0.018 U 0.0007 U 0.65 U
Methylene chloride 75�09�2 0.05 51 100 500 1,000 0.11 JB 0.0092 B 0.12 JB 0.11 JB 0.0057 JB 0.11 JB 0.0072 JB 0.56 JB 0.032 B 0.099 JB 0.56 JB 0.0069 JB 0.014 B 0.13 JB
4�Methyl�2�Pentanone 108�10�1 ��� ��� ��� ��� ��� 0.67 U 0.017 U 0.69 U 0.62 U 0.013 U 0.62 U 0.017 U 3.2 U 0.062 U 0.62 U 3.4 U 0.018 U 0.00047 U 0.65 UNaphthalene 91�20�3 ��� ��� ��� ��� ��� NA NA NA NA NA NA NA NA NA NA NA NA NA NA
Propylbenzene�n 103�65�1 3.9 100 100 500 1,000 NA NA NA NA NA NA NA NA NA NA NA NA NA NA
Sec�Butylbenzene 135�98�8 11 100 100 500 1,000 NA NA NA NA NA NA NA NA NA NA NA NA NA NATert�Butylbezene 98�06�6 5.9 100 100 500 1,000 NA NA NA NA NA NA NA NA NA NA NA NA NA NA
Tetrachloroethene 127�18�4 1.3 5.5 19 150 300 0.67 U 0.0087 U 0.69 U 0.62 U 0.0064 U 0.62 U 0.0087 U 3.2 U 0.006 J 0.62 U 3.4 U 0.0089 U 0.0007 U 0.65 U
Toluene 108�88�3 0.7 100 100 500 1,000 0.22 J 0.0013 J 0.12 J 0.62 U 0.00073 J 0.62 U 0.0087 U 3.2 U 0.024 J 0.62 U 3.4 U 0.0089 U 0.026 0.65 U
Trichloroethene 79�01�6 0.47 10 21 200 400 0.67 U 0.0087 U 0.69 U 0.62 U 0.0064 U 0.62 U 0.0087 U 3.2 U 0.031 U 0.62 U 3.4 U 0.0089 U 0.00035 U 0.65 U
Tetramethylbenzene�1,2,4,5 95�93�2 ��� ��� ��� ��� ��� NA NA NA NA NA NA NA NA NA NA NA NA NA NA
Vinyl Chloride 75�01�4 0.02 0.21 0.9 13 27 0.67 U 0.0087 U 0.69 U 0.62 U 0.0064 U 0.62 U 0.0087 U 3.2 U 0.031 U 0.62 U 3.4 U 0.0089 U 0.00035 U 0.65 U
1,2�Xylene (o�Xylene) 95�47�6 0.26 100 100 500 1,000 NA NA NA NA NA NA NA NA NA NA NA NA NA NA
1,3�Xylene (m�Xylene) 108�38�3 0.26 100 100 500 1,000 NA NA NA NA NA NA NA NA NA NA NA NA NA NAXylene (m,p�Xylene) 108�38�3 0.26 100 100 500 1,000 NA NA NA NA NA NA NA NA NA NA NA NA NA NA
Xylene (total) 1330�20�7 0.26 100 100 500 1,000 0.52 J 0.0089 0.22 J 0.41 J 0.0066 0.62 U 0.0087 U 3.2 U 0.28 0.28 J 3.4 U 0.0089 U 0.18 0.65 U
SVOCs
1,2�Dichlorobenzene 95�50�1 1.1 100 100 500 1,000 1.7 U 0.57 U 0.45 U 0.4 U 0.4 U 0.41 U 0.57 U 0.41 U 3.2 U 1.6 U 1.8 U 0.59 U 0.064 U 0.42 U
1,2�Diphenylhydrazine 122�66�7 ��� ��� ��� ��� ��� NA NA NA NA NA NA NA NA NA NA NA NA NA NA
1,2,4�Trichlorobenzene 120�82�1 ��� ��� ��� ��� ��� 1.7 U 0.57 U 0.45 U 0.4 U 0.4 U 0.41 U 0.57 U 0.41 U 3.2 U 1.6 U 1.8 U 0.59 U 0.064 U 0.42 U
2�Methylnaphthalene 91�57�6 ��� ��� ��� ��� ��� 1 J 0.57 U 1.1 0.36 J 0.4 U 2.2 0.57 U 0.44 2.6 J 1.7 4.4 0.59 U 2.9 1
2�Nitrophenol 88�75�5 ��� ��� ��� ��� ��� 1.7 U 0.57 U 0.45 U 0.4 U 0.4 U 0.41 U 0.57 U 0.41 U 3.2 U 1.6 U 1.8 U 0.59 U 0.13 U 0.42 U
2,4�Dimethylphenol 105�67�9 ��� ��� ��� ��� ��� 1.7 U 0.57 U 0.45 U 0.4 U 0.4 U 0.41 U 0.57 U 0.41 U 3.2 U 1.6 U 1.8 U 0.59 U 0.2 U 0.42 U
2,6�Dinitrotoluene 606�20�2 ��� ��� ��� ��� ��� 1.7 U 0.57 U 0.45 U 0.4 U 0.4 U 0.41 U 0.57 U 0.41 U 3.2 U 1.6 U 1.8 U 0.59 U 0.07 U 0.42 U
3�Nitroanaline 99�09�2 ��� ��� ��� ��� ��� 8.5 U 2.8 U 2.2 U 1.9 U 1.9 U 2 U 2.7 U 2 U 16 U 7.7 U 8.8 U 2.8 U 0.079 U 2 U
4�Chloroanaline 106�47�8 ��� ��� ��� ��� ��� 1.7 U 0.57 U 0.45 U 0.4 U 0.4 U 0.41 U 0.57 U 0.41 U 3.2 U 1.6 U 1.8 U 0.59 U 0.12 U 0.42 U
4�Nitroaniline 100�01�6 ��� ��� ��� ��� ��� 3.5 U 1.1 U 0.89 U 0.8 U 0.8 U 0.81 U 1.1 U 0.82 U 6.4 U 3.2 U 3.6 U 1.2 U 0.055 U 0.84 U
Acenaphthene 83�32�9 20 100 100 500 1,000 2.2 0.57 U 0.83 0.95 0.4 U 0.62 0.57 U 0.29 J 1.7 J 0.93 J 6.8 0.59 U 0.89 1.2
Acenaphthylene 208�96�8 100 100 100 500 1,000 0.96 J 0.57 U 0.41 J 0.4 U 0.4 U 0.21 J 0.57 U 0.13 J 0.62 J 0.26 J 2.9 0.59 U 0.047 U 0.42 U
Anthracene 120�12�7 100 100 100 500 1,000 2.1 0.57 U 0.28 J 0.35 J 0.4 U 0.15 J 0.57 U 0.29 J 3.5 2 4.1 0.59 U 0.5 0.52
Benzo (a) anthracene 56�55�3 1 1 1 5.6 11 1.8 0.57 U 0.18 J 0.29 J 0.4 U 0.13 J 0.57 U 0.58 7.5 3.9 4.1 0.59 U 0.74 0.54
Benzo (a) pyrene 50�32�8 1 1 1 1 1.1 1.7 J 0.57 U 0.13 J 0.65 0.4 U 0.17 J 0.57 U 0.5 6.7 4 11 0.59 U 0.81 0.58
Benzo (b) fluoranthene 205�99�2 1 1 1 5.6 11 1.6 J 0.57 U 0.21 J 0.36 J 0.4 U 0.41 U 0.57 U 0.36 J 5.5 3 4.5 0.59 U 0.81 0.48
Benzo (g,h,i) perylene 191�24�2 100 100 100 500 1,000 1.3 J 0.57 U 0.13 J 0.6 0.4 U 0.13 J 0.57 U 0.23 J 3.9 2.4 13 0.59 U 0.61 0.36 J
Benzo (k) fluoranthene 207�08�9 0.8 1 3.9 56 110 0.89 J 0.57 U 0.18 J 0.35 J 0.4 U 0.13 J 0.57 U 0.45 5.3 3.4 5.7 0.59 U 0.65 0.44
Benzyl alcohol 100�51�6 ��� ��� ��� ��� ��� 1.7 U 0.57 U 0.45 U 0.4 U 0.4 U 0.41 U 0.57 U 0.41 U 3.2 U 1.6 U 1.8 U 0.59 U 0.072 U 0.42 U
bis(2�chloroethoxy)methane 111�91�1 ��� ��� ��� ��� ��� 1.7 U 0.57 U 0.45 U 0.4 U 0.4 U 0.41 U 0.57 U 0.41 U 3.2 U 1.6 U 1.8 U 0.59 U 0.065 U 0.42 U
bis(2�ethylhexyl)phthalate 117�81�7 ��� ��� ��� ��� ��� 1.4 J 0.57 U 0.45 U 0.4 U 0.4 U 0.41 U 0.57 U 0.41 U 3.2 U 1.6 U 1.8 U 0.59 U 0.2 J 0.3 J
Butylbenzylphthalate 85�68�7 ��� ��� ��� ��� ��� 1.7 U 0.57 U 0.45 U 0.4 U 0.4 U 0.41 U 0.57 U 0.41 U 0.84 J 1.6 U 1.8 U 0.59 U 0.049 U 0.42 U
Carbozole 86�74�8 ��� ��� ��� ��� ��� 0.38 J 0.57 U 0.45 U 0.4 U 0.4 U 0.41 U 0.57 U 0.41 U 1.3 J 0.33 J 1.8 U 0.59 U 0.056 U 0.42 U
Chrysene 218�01�9 1 1 3.9 56 110 2.0 0.57 U 0.27 J 0.31 J 0.4 U 0.13 J 0.57 U 0.64 7.5 4.2 4.2 0.59 U 0.84 0.59
Dibenzo (a,h) anthracene 53�70�3 0.33 0.33 0.33 0.56 1.1 1.7 U 0.57 U 0.45 U 0.082 J 0.4 U 0.41 U 0.57 U 0.1 J 1.7 J 0.86 J 1.8 0.59 U 0.23 J 0.081 J
Dibenzofuran 132�64�9 ��� ��� ��� ��� ��� 1 J 0.57 U 0.52 0.75 0.4 U 0.16 J 0.57 U 0.14 J 1.2 J 0.62 J 1.8 0.59 U 0.62 0.83
Fluoranthene 206�44�0 100 100 100 500 1,000 5.5 0.57 U 0.54 0.45 0.4 U 0.24 J 0.57 U 0.99 15 8.5 6.5 0.59 U 1.5 0.96
Fluorene 86�73�7 30 100 100 500 1,000 3 0.57 U 1.1 1.6 0.4 U 0.3 J 0.57 U 0.25 J 2.2 J 1.1 J 5.3 0.59 U 1.1 1.5
Hexachloroethane 67�72�1 ��� ��� ��� ��� ��� 1.7 U 0.57 U 0.45 U 0.4 U 0.4 U 0.41 U 0.57 U 0.41 U 3.2 U 1.6 U 1.8 U 0.59 U 0.067 U 0.42 U
Indeno (1,2,3�cd) pyrene 193�39�5 0.5 0.5 0.5 5.6 11 0.84 J 0.57 U 0.1 J 0.35 J 0.4 U 0.081 J 0.57 U 0.2 J 3.8 2.0 7.2 0.59 U 0.45 0.29 J
Isophorone 78�59�1 ��� ��� ��� ��� ��� 1.7 U 0.57 U 0.45 U 0.4 U 0.4 U 0.41 U 0.57 U 0.41 U 3.2 U 1.6 U 1.8 U 0.59 U 0.068 U 0.42 U
n�Nitrosodiphenylamine 86�30�6 ��� ��� ��� ��� ���� 1.7 U 0.57 U 0.45 U 0.4 U 0.4 U 0.41 U 0.57 U 0.41 U 3.2 U 1.6 U 1.8 U 0.59 U 0.057 U 0.42 U
Naphthalene 91�20�3 12 100 100 500 1,000 1.6 J 0.57 U 0.46 0.4 U 0.4 U 0.93 0.57 U 0.35 J 1.6 J 1.6 4.2 0.59 U 1.5 0.64
Nitrobenzene 98�95�3 ��� ��� ��� ��� ��� 1.7 U 0.57 U 0.45 U 0.4 U 0.4 U 0.41 U 0.57 U 0.41 U 3.2 U 1.6 U 1.8 U 0.59 U 0.046 U 0.42 U
o�Cresol(s) (2�Methylphenol) 95�48�7 0.33 100.00 100 500 1,000 1.7 U 0.57 U 0.45 U 0.4 U 0.4 U 0.41 U 0.57 U 0.41 U 3.2 U 1.6 U 1.8 U 0.59 U 0.1 U 0.42 U
m,p�Cresol(s) (3&4�Methylphenol) 106�44�5 0.33 34 100 500 1,000 NA NA NA NA NA NA NA NA NA NA NA NA NA NA
p�Cresol(s) (4�Methylphenol) 106�44�5 0.33 34 100 500 1,000 1.7 U 0.57 U 0.45 U 0.4 U 0.4 U 0.41 U 0.57 U 0.41 U 3.2 U 1.6 U 1.8 U 0.59 U 0.2 U 0.42 U
Pentachlorophenol 87�86�5 0.8 2.4 6.7 6.7 55 8.5 U 2.8 U 2.2 U 1.9 U 1.9 U 2 U 2.7 U 2 U 16 U 7.7 U 8.8 U 2.8 U 0.33 U 2 U
Phenanthrene 85�01�8 100 100 100 500 1,000 5.3 0.57 U 0.52 1.3 0.4 U 0.31 J 0.57 U 1.1 11 6.1 10 0.59 U 1.9 1.9
Phenol 108�95�2 0.33 100 100 500 1,000 1.7 U 0.57 U 0.45 U 0.4 U 0.4 U 0.41 U 0.57 U 0.41 U 3.2 U 1.6 U 1.8 U 0.59 U 0.11 U 0.42 U
Pyrene 129�00�0 100 100 100 500 1,000 5.9 0.57 U 0.58 0.93 0.4 U 0.4 J 0.57 U 1.2 11 7.3 9.8 0.59 U 1.9 1.8
TPH # Diesel Range Organics
Fuel Oil #2 ��� ��� ��� ��� ��� NA NA NA NA NA NA NA NA NA NA NA NA NA NA
Total DRO TPH ��� ��� ��� ��� ��� NA NA NA NA NA NA NA NA NA NA NA NA NA NA
Unknown DRO TPH ��� ��� ��� ��� ��� NA NA NA NA NA NA NA NA NA NA NA NA NA NA
PCBs/Pesticides
Aroclor 1242 53469�21�9 0.1 1 1 1 25 0.15 NA 0.023 U 0.021 U NA 0.021 U NA 0.021 U NA 0.021 U 0.023 U NA 0.0034 U 0.022 U
Aroclor 1248 12672�29�6 0.1 1 1 1 25 0.022 U NA 0.023 U 0.021 U NA 0.021 U NA 0.021 U NA 0.021 U 0.023 U NA 0.0065 J 0.028
Aroclor 1260 11096�82�5 0.1 1 1 1 25 0.098 NA 0.023 U 0.021 U NA 0.021 U NA 0.022 NA 0.021 U 0.023 U NA 0.0046 U 0.046
Total PCBs/Pesticides ��� ��� ��� ��� ��� ��� 0.38 NA NA NA 0.168 NA NA 0.023 J 0.204
Metals
Aluminum 7429�90�5 ��� ��� ��� ��� ��� 9,260 NA 3,960 1,130 NA 3,420 NA 5,730 NA 2,630 4,210 NA 2,700 4,220
Arsenic 7440�38�2 13 16 16 16 16 9.8 J NA 43.2 9.2 J NA 11.1 J NA 3.2 J NA 8.9 J 6.1 J NA 5.6 J 33.3
Barium 7440�39�3 350 350 400 400 10,000 202 NA 150 18.3 NA 142 NA 60.2 NA 57.8 102 NA 58.3 108
Beryllium 7440�41�7 7.2 14 72 590 2,700 2.6 U NA 2.8 U 2.5 U NA 2.8 U NA 2.6 U NA 2.6 U 2.9 U NA 0.66 U 2.2 U
Cadmium 7440�43�9 2.5 2.5 4.3 9.3 60 2.2 J NA 4.2 U 3.7 U NA 4.2 U NA 3.9 U NA 3.9 U 4.4 U NA 1.3 U 1.3 J
Calcium 7440�70�2 ��� ��� ��� ��� ��� 22,300 NA 15,000 216,000 NA 4,230 NA 6,830 NA 18,500 81,300 NA 7,870 25,600
Chromium 7440�47�3 27.2 NA 11.3 61.4 NA 8 NA 19.9 NA 7.6 6 NA 11.1 16.1
Cobalt 7440�48�4 ��� ��� ��� ��� ��� 8.5 NA 7.1 1.7 J NA 4.4 NA 6.6 NA 4.2 3.1 NA 5.4 6.3
Copper 7440�50�8 50 270 270 270 10,000 159 NA 49.5 37.4 NA 204 NA 26.1 NA 131 76 NA 42.3 85
Iron 7439�89�6 ��� ��� ��� ��� ��� 32,100 NA 15,100 7,750 NA 8,290 NA 13,400 NA 9,460 7,440 NA 9,620 18,300
Lead 7439�92�1 63 400 400 1,000 3,900 283 NA 856 93.9 NA 265 NA 52.8 NA 222 139 NA 129 232
Magnesium 7439�95�4 ��� ��� ��� ��� ��� 5,990 NA 1,830 2,250 NA 948 NA 3,610 NA 705 3,840 NA 1,400 1,830
Manganese 7439�96�5 1600 2,000 2,000 10,000 10,000 267 NA 139 133 NA 141 NA 161 NA 93.1 282 NA 151 276
Mercury (elemental) 7439�97�6 0.18 0.81 0.81 2.8 5.7 0.84 NA 1.9 0.14 NA 1.2 NA 0.62 NA 0.28 0.085 NA 0.094 0.49
Nickel 7440�02�0 30 140 310 310 10,000 34.5 NA 16.8 5.1 J NA 10.4 NA 16.3 NA 13.7 10.4 NA 16.4 21.7
Potassium 7440�09�7 ��� ��� ��� ��� ��� 1980 NA 448 285 NA 554 NA 1100 NA 306 333 NA 310 574
Selenium 7782�49�2 3.9 36 180 1,500 6,800 20.8 U NA 17.4 J 20 U NA 22.4 U NA 20.4 U NA 20.7 U 23.4 U NA 2.1 U 6 J
Silver 7440�22�4 2 36 180 1,500 6,800 3.9 U NA 5.9 3.7 U NA 0.7 J NA 3.8 U NA 3.9 U 4.4 U NA 0.42 U 3.3 U
Sodium 7440�23�5 ��� ��� ��� ��� ��� 466 NA 171 192 NA 407 NA 208 NA 114 J 533 NA 131 169
Vanadium 7440�62�2 ��� ��� ��� ��� ��� 32 NA 22.7 5.3 NA 16.4 NA 25.6 NA 10.3 11 NA 12.6 18.9
Zinc 7440�66�6 109 2200 10000 10000 10000 779 NA 1,090 69.2 NA 106 NA 57.4 NA 79.9 211 NA 73.1 264
Miscellaneous
Percent Solid (%) ��� ��� ��� ��� ��� ��� NA NA NA NA NA NA NA NA NA NA NA NA NA NA
NOTES:
NYSDEC Soil Cleanup Objective Tables can be found in Tables 375�6.8(a) and 375�6.8(b) dated 14 December 2006.
Sample data for ELM, Cosmos, and Tradewind were provided in the Phase II Investigation Report, 400 Carroll Street by ELM dated May 2005.
Sample data for PW Grosser were provided in the PW Grosser Draft Subsurface Investigation Summary Report dated 16 June 2011.
Sample data for Zeb Environmental were provided in an environmental investigatiton provided by Sive Padget & Riesel, LLP.
Italicized values indicate method detection limit (MDL) exceeds criteria.
Cosmos Environmental Services Samples:
^ : EcoTest Laboratories reported that it could not separate the isonomers for benzo(b)fluoranthene and benzo(k)fluoranthene. Therefore, the sum is split evenly between the two analytes.
1: Elevated detection limits due to interference in sample.
2: Sample was a composite of TP�1, TP�3, TP�6, and TP�8.
Qualifiers:
E:Concentration of analyte exceeds the range of the calibration curve and/or linear range of the instrument.
J:Estimated value. This represents an estimated concentration for Tentatively Identified Compounds (TICs).
U:The analytical results is not detected above the Methof Detection Limit (MDL). All MDLs are lower than the lowest calibration standard concentration.
ND:Not detected at the reporting limit (RL) for the sample.
CAS No.UNRESTRICTE
D USE
Environmental Liability Management of New York, LLC
Protection of Public Health
\\Langan.com\data\EP\data5\100287501\Engineering Data\Environmental\Reports\2013�07 � OER Phase II RIWP REVISED (363 Bond�400 Carroll)\Tables\Table 5 � Historical Soil Data for 400 Carroll�OVERALL TABLE
7/9/20133:41 PM
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TABLE 5HISTORICAL SOIL ANALYTICAL RESULTS
Proposed Bond Street Development
400 Carroll Street
Brooklyn, New York
Consultant:
Sample ID: SUBPART 375#6 (Revised Brownfields)
Laboratory Sample Number:
Sampling Date: Unrestricted # Restricted # Restricted # Restricted #
Sampling Depth (ft): Residential Residential Commercial Industrial
Units: (mg/kg) (mg/kg) (mg/kg) (mg/kg) (mg/kg)
VOCs
1,1,1�Trichloroethane 71�55�6 0.68 100 100 500 1,0001,1�Dichloroethane 75�34�3 0.27 19 26 240 4801,1�Dichloroethene 75�35�4 0.33 100 100 500 1,0001,2�Dichloroethane 107�06�2 0.02 2.3 3.1 30 60
1,2�Dichloroethene (cis) 156�59�2 0.25 59 100 500 1,0001,2�Dichloroethene (trans) 156�60�5 0.19 100 100 500 1,000
1,2,3�Trichlorobenzene 87�61�6 ��� ��� ��� ��� ���
1,2,3�Trichloropropane 96�18�4 ��� ��� ��� ��� ���1,2,4�Trichlorobenzene 120�82�1 ��� ��� ��� ��� ���1,2,4�Trimethylbenzene 95�63�6 3.6 47 52 190 380
1,3,5�Trimethylbenzene 108�67�8 8.4 47 52 190 380
4�Isopropyltoluene 99�87�6 ��� ��� ��� ��� ���
Acetone 67�64�1 0.05 100 100 500 1,000
Benzene 71�43�2 0.06 2.9 4.8 44 89
n�Butylbenzene 104�51�8 12 100 100 500 1,000
Carbon Disulfide 75�15�0 ��� ��� ��� ��� ���
Carbon tetrachloride 56�23�5 0.76 1.4 2.4 22 44
Chlorobenzene 108�90�7 1.1 100 100 500 1,000
Chloroform 67�66�3 0.37 10.00 49 350 700Diethylbenzene�p 105�05�5 ��� ��� ��� ��� ���
Ethylbenzene 100�41�4 1 30 41 390 780
p�Ethyltoluene 622�96�8 ��� ��� ��� ��� ���
Isopropyl Benzene 98�82�8 ��� ��� ��� ��� ���p�Isopropyltoluene 99�87�6 ��� ��� ��� ��� ���
Methyl ethyl ketone (MEK / 2�butanone) 78�93�3 0.12 100 100 500 1,000
Methylene chloride 75�09�2 0.05 51 100 500 1,000
4�Methyl�2�Pentanone 108�10�1 ��� ��� ��� ��� ���Naphthalene 91�20�3 ��� ��� ��� ��� ���
Propylbenzene�n 103�65�1 3.9 100 100 500 1,000
Sec�Butylbenzene 135�98�8 11 100 100 500 1,000Tert�Butylbezene 98�06�6 5.9 100 100 500 1,000
Tetrachloroethene 127�18�4 1.3 5.5 19 150 300
Toluene 108�88�3 0.7 100 100 500 1,000
Trichloroethene 79�01�6 0.47 10 21 200 400Tetramethylbenzene�1,2,4,5 95�93�2 ��� ��� ��� ��� ���
Vinyl Chloride 75�01�4 0.02 0.21 0.9 13 27
1,2�Xylene (o�Xylene) 95�47�6 0.26 100 100 500 1,000
1,3�Xylene (m�Xylene) 108�38�3 0.26 100 100 500 1,000Xylene (m,p�Xylene) 108�38�3 0.26 100 100 500 1,000
Xylene (total) 1330�20�7 0.26 100 100 500 1,000
SVOCs
1,2�Dichlorobenzene 95�50�1 1.1 100 100 500 1,000
1,2�Diphenylhydrazine 122�66�7 ��� ��� ��� ��� ���
1,2,4�Trichlorobenzene 120�82�1 ��� ��� ��� ��� ���
2�Methylnaphthalene 91�57�6 ��� ��� ��� ��� ���
2�Nitrophenol 88�75�5 ��� ��� ��� ��� ���
2,4�Dimethylphenol 105�67�9 ��� ��� ��� ��� ���
2,6�Dinitrotoluene 606�20�2 ��� ��� ��� ��� ���
3�Nitroanaline 99�09�2 ��� ��� ��� ��� ���
4�Chloroanaline 106�47�8 ��� ��� ��� ��� ���
4�Nitroaniline 100�01�6 ��� ��� ��� ��� ���
Acenaphthene 83�32�9 20 100 100 500 1,000
Acenaphthylene 208�96�8 100 100 100 500 1,000
Anthracene 120�12�7 100 100 100 500 1,000
Benzo (a) anthracene 56�55�3 1 1 1 5.6 11
Benzo (a) pyrene 50�32�8 1 1 1 1 1.1
Benzo (b) fluoranthene 205�99�2 1 1 1 5.6 11
Benzo (g,h,i) perylene 191�24�2 100 100 100 500 1,000
Benzo (k) fluoranthene 207�08�9 0.8 1 3.9 56 110
Benzyl alcohol 100�51�6 ��� ��� ��� ��� ���
bis(2�chloroethoxy)methane 111�91�1 ��� ��� ��� ��� ���
bis(2�ethylhexyl)phthalate 117�81�7 ��� ��� ��� ��� ���
Butylbenzylphthalate 85�68�7 ��� ��� ��� ��� ���
Carbozole 86�74�8 ��� ��� ��� ��� ���
Chrysene 218�01�9 1 1 3.9 56 110
Dibenzo (a,h) anthracene 53�70�3 0.33 0.33 0.33 0.56 1.1
Dibenzofuran 132�64�9 ��� ��� ��� ��� ���
Fluoranthene 206�44�0 100 100 100 500 1,000
Fluorene 86�73�7 30 100 100 500 1,000
Hexachloroethane 67�72�1 ��� ��� ��� ��� ���
Indeno (1,2,3�cd) pyrene 193�39�5 0.5 0.5 0.5 5.6 11
Isophorone 78�59�1 ��� ��� ��� ��� ���
n�Nitrosodiphenylamine 86�30�6 ��� ��� ��� ��� ����
Naphthalene 91�20�3 12 100 100 500 1,000
Nitrobenzene 98�95�3 ��� ��� ��� ��� ���
o�Cresol(s) (2�Methylphenol) 95�48�7 0.33 100.00 100 500 1,000
m,p�Cresol(s) (3&4�Methylphenol) 106�44�5 0.33 34 100 500 1,000
p�Cresol(s) (4�Methylphenol) 106�44�5 0.33 34 100 500 1,000
Pentachlorophenol 87�86�5 0.8 2.4 6.7 6.7 55
Phenanthrene 85�01�8 100 100 100 500 1,000
Phenol 108�95�2 0.33 100 100 500 1,000
Pyrene 129�00�0 100 100 100 500 1,000
TPH # Diesel Range Organics
Fuel Oil #2 ��� ��� ��� ��� ���
Total DRO TPH ��� ��� ��� ��� ���
Unknown DRO TPH ��� ��� ��� ��� ���
PCBs/Pesticides
Aroclor 1242 53469�21�9 0.1 1 1 1 25
Aroclor 1248 12672�29�6 0.1 1 1 1 25
Aroclor 1260 11096�82�5 0.1 1 1 1 25
Total PCBs/Pesticides ��� ��� ��� ��� ��� ���
Metals
Aluminum 7429�90�5 ��� ��� ��� ��� ���
Arsenic 7440�38�2 13 16 16 16 16
Barium 7440�39�3 350 350 400 400 10,000
Beryllium 7440�41�7 7.2 14 72 590 2,700
Cadmium 7440�43�9 2.5 2.5 4.3 9.3 60
Calcium 7440�70�2 ��� ��� ��� ��� ���
Chromium 7440�47�3
Cobalt 7440�48�4 ��� ��� ��� ��� ���
Copper 7440�50�8 50 270 270 270 10,000
Iron 7439�89�6 ��� ��� ��� ��� ���
Lead 7439�92�1 63 400 400 1,000 3,900
Magnesium 7439�95�4 ��� ��� ��� ��� ���
Manganese 7439�96�5 1600 2,000 2,000 10,000 10,000
Mercury (elemental) 7439�97�6 0.18 0.81 0.81 2.8 5.7
Nickel 7440�02�0 30 140 310 310 10,000
Potassium 7440�09�7 ��� ��� ��� ��� ���
Selenium 7782�49�2 3.9 36 180 1,500 6,800
Silver 7440�22�4 2 36 180 1,500 6,800
Sodium 7440�23�5 ��� ��� ��� ��� ���
Vanadium 7440�62�2 ��� ��� ��� ��� ���
Zinc 7440�66�6 109 2200 10000 10000 10000
Miscellaneous
Percent Solid (%) ��� ��� ��� ��� ��� ���
NOTES:
NYSDEC Soil Cleanup Objective Tables can be found in Tables 375�6.8(a) and 375�6.8(b) dated 14 December 2006.
Sample data for ELM, Cosmos, and Tradewind were provided in the Phase II Investigation Report, 400 Carroll Street by ELM dated May 2005.
Sample data for PW Grosser were provided in the PW Grosser Draft Subsurface Investigation Summary Report dated 16 June 2011.
Sample data for Zeb Environmental were provided in an environmental investigatiton provided by Sive Padget & Riesel, LLP.
Italicized values indicate method detection limit (MDL) exceeds criteria.
Cosmos Environmental Services Samples:
^ : EcoTest Laboratories reported that it could not separate the isonomers for benzo(b)fluoranthene and benzo(k)fluoranthene. Therefore, the sum is split evenly between the two analytes.
1: Elevated detection limits due to interference in sample.
2: Sample was a composite of TP�1, TP�3, TP�6, and TP�8.
Qualifiers:
E:Concentration of analyte exceeds the range of the calibration curve and/or linear range of the instrument.
J:Estimated value. This represents an estimated concentration for Tentatively Identified Compounds (TICs).
U:The analytical results is not detected above the Methof Detection Limit (MDL). All MDLs are lower than the lowest calibration standard concentration.
ND:Not detected at the reporting limit (RL) for the sample.
CAS No.UNRESTRICTE
D USE
Protection of Public Health
TP�1/3�3.5 TP�3/4�7 TP�4/4�5 TP�5/1.5�3 TP�6/2.7�4.7 GP�02 GP�04 GP�10 GP�11 P�9 P�9 P�10 P�10
207935�020 207936�001 207936�002 207936�003 207936�004 L1104348�02 L1104348�04 L1104656�02 L1104656�03 1204165�1 1204165�2 1204165�3 1204165�4
10/27/2004 10/27/2004 10/27/2004 10/27/2004 10/27/2004 3/30/2011 3/30/2011 4/6/2011 4/6/2011 4/12/2012 4/12/2012 4/12/2012 4/12/20123�3.5 4�7 4�5 1.5�3 2.7�4.7 25�30 25�30 25�30 25�30 3.5�5 6.5�7 3�4 7�8
mg/kg Q mg/kg Q mg/kg Q mg/kg Q mg/kg Q mgkg Q mg/kg Q mg/kg Q mg/kg Q mg/kg Q mg/kg Q mg/kg Q mg/kg Q
0.58 U 0.00061 U 0.11 U 0.42 U 0.47 U 0.003 U 0.003 U 0.13 U 0.003 U 0.245 U 0.0104 U 0.077 U 0.0738 U0.58 U 0.00049 U 0.051 U 0.2 U 0.22 U 0.004 U 0.005 U 0.19 U 0.005 U 0.142 U 0.00918 U 0.0444 U 0.0426 U0.58 U 0.00049 U 0.09 U 0.35 U 0.39 U 0.003 U 0.003 U 0.13 U 0.003 U 0.175 U 0.0108 U 0.0548 U 0.0525 U0.58 U 0.00061 U 0.076 U 0.3 U 0.33 U 0.003 U 0.003 U 0.13 U 0.003 U 0.236 U 0.0115 U 0.074 U 0.071 U
0.58 U 0.00037 U 0.088 U 0.35 U 0.38 U 0.003 U 0.003 U 0.13 U 0.003 U 0.198 U 0.0106 U 0.0622 U 0.0596 U0.58 U 0.00074 U 0.06 U 0.24 U 0.26 U 0.004 U 0.005 U 0.19 U 0.005 U 0.127 U 0.0104 U 0.04 U 0.0383 U
NA NA NA NA NA 0.015 U 0.016 U 0.63 U 0.016 U 0.17 U 0.0101 U 0.0533 U 0.0511 U
NA NA NA NA NA 0.029 U 0.032 U 1.3 U 0.032 U 2.83 0.0103 U 0.47 J 0.0767 UNA NA NA NA NA NA NA NA NA 0.212 U 0.0107 U 0.0666 U 0.0639 UNA NA NA NA NA 0.015 U 0.016 U 0.63 U 0.016 U 0.454 J 0.0125 U 0.249 J 0.0625 U
NA NA NA NA NA 0.015 U 0.016 U 0.63 U 0.016 U 0.203 U 0.0124 U 0.133 J 0.0611 U
NA NA NA NA NA NA NA NA NA 1.43 J 0.0148 J 0.718 J 0.0483 U
1.5 U 0.063 0.24 U 2.2 J 2.4 J 0.029 U 0.032 U 1.3 U 0.032 U 1.38 U 0.0387 U 0.432 U 0.415 U
0.58 U 0.00061 U 0.065 U 0.78 J 0.46 J 0.003 U 0.003 U 0.13 U 0.008 0.203 U 0.0107 U 0.112 J 0.0611 U
NA NA NA NA NA 0.003 U 0.0053 U 0.13 U 0.003 U 10.1 0.0189 J 0.483 J 0.515 J
0.58 U 0.003 J 0.045 U 0.18 U 0.34 J 0.029 U 0.032 U 1.3 U 0.032 U 0.189 U 0.0138 J 0.0592 U 0.0568 U
0.58 U 0.00037 U 0.068 U 0.27 U 0.3 U 0.003 U 0.003 U 0.13 U 0.003 U 0.208 U 0.0104 U 0.0651 U 0.0625 U
0.58 U 0.00049 U 0.054 U 0.21 U 0.23 U 0.003 U 0.003 U 0.13 U 0.003 U 0.227 U 0.0123 U 0.071 U 0.0682 U
0.58 U 0.00074 U 0.068 U 0.27 U 0.3 U 0.006 0.006 0.19 U 0.005 U 0.217 U 0.0116 U 0.0681 U 0.0653 UNA NA NA NA NA 0.012 U 0.029 0.51 U 0.013 U 2.5 0.0114 U 0.351 J 0.447 J
0.58 U 0.015 0.059 U 0.64 J 0.9 J 0.003 U 0.003 U 0.31 0.005 0.194 U 0.0102 U 0.137 J 0.0582 U
NA NA NA NA NA NA NA NA NA 0.633 J 0.0123 U 0.317 J 0.0554 U
NA NA NA NA NA 0.003 U 0.003 U 0.13 U 0.005 U 4.44 0.0122 U 0.226 J 0.649 JNA NA NA NA NA 0.003 U 0.003 U 0.13 U 0.003 U 1.43 J 0.0148 J 0.718 J 0.0483 U
0.58 U 0.00074 U 0.2 U 0.77 U 0.85 U 0.029 U 0.032 U 1.3 U 0.032 U 0.906 U 0.0208 U 0.284 U 0.273 U
0.11 JB 0.015 B 0.16 JB 0.71 JB 0.67 JB 0.029 U 0.032 U 1.3 U 0.032 U 0.184 U 0.0108 U 0.0577 U 0.0554 U
0.58 U 0.00049 U 0.11 U 0.41 U 0.46 U 0.029 U 0.032 U 1.3 U 0.032 U 0.859 U 0.0279 U 0.269 U 0.258 UNA NA NA NA NA 0.016 0.016 U 5.6 0.016 U 0.156 U 0.00798 U 0.666 J 0.0469 U
NA NA NA NA NA 0.003 U 0.003 U 0.13 U 0.004 9.2 0.0211 J 0.351 J 1.08
NA NA NA NA NA 0.003 U 0.003 U 0.13 U 0.003 U 8.68 0.0125 U 0.537 J 0.96NA NA NA NA NA 0.015 U 0.016 U 0.63 U 0.016 U 2.73 0.0119 U 0.375 J 0.322 J
0.58 U 0.00074 U 0.052 U 0.2 U 0.22 U 0.003 U 0.003 U 0.13 U 0.003 U 0.278 U 0.0123 U 0.0873 U 0.0838 U
0.58 U 0.0059 J 0.044 U 0.89 J 0.37 J 0.004 U 0.005 U 0.19 U 0.005 U 0.212 U 0.0109 U 0.102 J 0.0639 U
0.58 U 0.00037 U 0.096 U 0.38 U 0.42 U 0.003 U 0.003 U 0.13 U 0.003 U 0.217 U 0.00999 U 0.0681 U 0.0653 UNA NA NA NA NA 0.012 U 0.028 0.51 U 0.013 U 30.2 0.115 2.16 3.12 0
0.58 U 0.00037 U 0.067 U 0.27 U 0.29 U 0.006 U 0.007 U 0.25 U 0.006 U 0.203 U 0.0126 U 0.0636 U 0.0611 U
NA NA NA NA NA 0.006 U 0.007 U 0.25 U 0.006 U 0.175 U 0.0126 U 0.0548 U 0.0525 U
NA NA NA NA NA NA NA NA NA 0.771 J 0.024 U 0.273 J 0.122 UNA NA NA NA NA 0.006 U 0.007 U 0.25 U 0.006 U 0.771 J 0.024 U 0.273 J 0.122 U
0.58 U 0.042 0.11 U 2.2 J 1.1 J ND ND ND ND NA NA NA NA
0.37 U 0.067 U 0.065 U 0.063 U 0.14 U 0.2 U 0.22 U 0.2 U 0.21 U 0.0389 U 0.0355 U 0.0366 U 0.035 U
NA NA NA NA NA NA NA NA NA 0.209 J 0.0347 U 0.0358 U 0.0342 U
0.37 U 0.067 U 0.065 U 0.063 U 0.14 U 0.2 U 0.22 U 0.2 U 0.21 U 0.455 J 0.0478 U 0.0493 U 0.0472 U
0.15 J 2.9 0.074 J 2.1 0.78 J 0.2 U 0.22 U 1.4 E 0.0085 U 0.0499 U 0.0746 J 0.963 0.045 U
0.37 U 0.14 U 0.13 U 0.13 U 0.29 U 0.8 U 0.88 U 0.44 U 0.46 U 0.0382 U 0.0349 U 0.036 U 0.0345 U
0.37 U 0.2 U 0.22 J 0.19 U 0.43 U 0.2 U 0.22 U 0.2 U 0.21 U 0.0526 U 0.048 U 0.405 J 0.0474 U
0.37 U 0.073 U 0.071 U 0.069 U 0.15 U 0.2 U 0.22 U 0.2 U 0.21 U 0.0518 U 0.0473 U 0.0488 U 0.0467 U
1.8 U 0.082 U 0.08 U 0.078 U 0.17 U 0.2 U 0.22 U 0.2 U 0.21 U 0.0216 U 0.0197 U 0.505 J 0.0195 U
0.37 U 0.13 U 0.12 U 0.12 U 0.27 U 0.2 U 0.22 U 0.2 U 0.21 U 0.0479 U 0.0437 U 0.0451 U 0.0432 U
0.73 U 0.057 U 0.056 U 0.054 U 0.12 U 0.28 U 0.31 U 0.2 U 0.21 U 0.123 U 0.112 U 0.116 U 0.111 U
0.15 J 0.34 J 0.67 0.69 1.2 0.2 U 0.29 1.4 E 0.093 4.41 0 0.0551 J 1.03 0.0477 U
0.092 J 0.21 J 0.047 U 0.52 0.75 J 0.2 U 0.22 U 0.048 0.0085 U 0.0433 U 0.0395 U 0.0408 U 0.039 U
0.37 U 0.22 J 0.31 J 0.66 1.5 0.2 U 0.22 U 0.17 0.033 3.43 0.158 J 0.0527 U 0.0505 U
0.37 U 0.4 0.28 J 1.5 0.95 0.2 U 0.22 U 0.0095 0.0085 U 3.03 0.118 J 0.759 0.048 U
0.37 U 0.42 0.22 J 1.7 0.64 J 0.2 U 0.22 U 0.0081 U 0.0085 U 5.84 0.189 J 0.782 0.0591 U
0.37 U 0.39 J 0.18 J 2.7 0.51 J 0.2 U 0.22 U 0.0081 U 0.0085 U 2.76 0.07 J 0.63 0.0471 U
0.37 U 0.29 J 0.12 J 1 0.63 J 0.2 U 0.22 U 0.0081 U 0.0085 U 7.14 0.152 J 0.814 0.0866 U
0.37 U 0.33 J 0.19 J 0.042 U 0.53 J 0.2 U 0.22 U 0.0081 U 0.0085 U 3.52 0.0964 J 0.615 0.0863 U
0.37 U 0.075 U 0.073 U 0.071 U 0.16 U 0.4 U 0.44 U 0.2 U 0.21 U 0.244 J 0.0677 U 0.0699 U 0.0669 U
0.37 U 0.068 U 0.066 U 0.064 U 0.14 U 0.2 U 0.22 U 0.22 U 0.23 U 0.123 J 0.0475 U 0.0491 U 0.0469 U
0.2 J 0.13 J 0.051 U 0.18 J 0.15 J 0.4 U 0.44 U 0.2 U 0.21 U 0.0824 U 0.123 J 0.185 J 0.0743 U
0.37 U 0.051 U 0.05 U 0.048 U 0.11 U 0.2 U 0.22 U 0.2 U 0.21 U 0.0664 U 0.0606 U 0.0626 U 0.0599 U
0.37 U 0.058 U 0.057 U 0.08 J 0.12 U 0.2 U 0.22 U 0.2 U 0.21 U 0.0725 U 0.0661 U 0.0682 U 0.0653 U
0.37 U 0.45 0.32 J 1.6 1.0 0.2 U 0.22 U 0.0091 0.0085 U 3.24 0.13 J 0.882 0.06 U
0.37 U 0.11 J 0.046 J 0.54 0.13 J 0.12 U 0.13 U 0.0081 U 0.0085 U 0.668 0.0641 U 0.0661 U 0.0633 U
0.16 J 0.17 J 0.43 0.49 0.69 J 0.2 U 0.22 U 0.2 U 0.21 U 0.042 U 0.0383 U 0.549 J 0.0379 U
0.062 J 0.91 0.8 2.2 1.9 0.2 U 0.22 U 0.038 0.029 0.0693 U 0.276 J 2 0.0625 U
0.25 J 0.26 J 0.81 0.73 1.9 0.2 U 0.22 U 0.48 0.0086 5.75 0.093 J 1.07 0.0456 U
0.37 U 0.07 U 0.068 U 0.066 U 0.15 U 0.2 U 0.22 U 0.032 U 0.034 U 0.056 U 0.0511 U 0.999 0.0505 U
0.37 U 0.22 J 0.11 J 0.92 0.39 J 0.2 U 0.22 U 0.0081 U 0.0085 U 3.57 0.0804 J 0.582 J 0.0524 U
0.37 U 0.071 U 0.069 U 0.068 U 0.15 U 0.2 U 0.22 U 0.18 U 0.19 U 2.75 0.0525 U 0.313 J 0.0518 U
0.37 U 0.059 U 0.058 U 0.056 U 0.12 U 0.6 U 0.66 U 0.16 U 0.17 U 0.0686 U 0.0626 U 0.0646 U 0.0618 U
0.11 J 0.53 0.066 U 1 2.2 0.2 U 0.22 U 4.0 E 0.0085 U 0.0506 U 0.0462 U 0.927 0.0456 U
0.37 U 0.048 U 0.046 U 0.045 U 0.1 U 0.2 U 0.22 U 0.18 U 0.19 U 0.797 0.0444 U 0.126 J 0.0439 U
0.37 U 0.11 U 0.1 U 0.1 U 0.22 U 0.24 U 0.26 U 0.2 U 0.21 U 0.045 U 0.0411 U 0.0424 U 0.0406 U
NA NA NA NA NA 0.24 U 0.26 U 0.29 U 0.31 U 0.0389 U 0.0355 U 0.0366 U 0.035 U
0.37 U 0.21 U 0.21 U 0.2 U 0.45 U NA NA NA NA 0.0389 U 0.0355 U 0.0366 U 0.035 U
1.8 U 0.34 U 0.33 U 0.32 U 0.72 U 0.8 U 0.88 U 0.032 U 0.034 U 0.477 U 0.435 U 0.449 U 0.43 U
0.24 J 0.87 0.18 J 1.5 3.5 0.2 U 0.22 U 0.73 0.16 8.94 0.436 J 2.36 0.0516 U
0.37 U 0.12 U 0.11 U 0.11 U 0.24 U 0.28 U 0.31 U 0.2 U 0.21 U 0.0328 U 0.03 U 0.0309 U 0.0296 U
0.092 J 0.91 0.74 2.5 3.4 0.2 U 0.22 U 0.036 0.029 13.6 E 0.441 J 1.94 0.042 U
NA NA NA NA NA NA NA NA NA NA NA NA NA
NA NA NA NA NA NA NA NA NA NA NA NA NA
NA NA NA NA NA NA NA NA NA NA NA NA NA
0.019 U 0.0036 U 0.0035 U 0.0035 U 0.0038 U NA NA NA NA NA NA NA NA
0.019 U 0.0032 U 0.0032 U 0.0031 U 0.0034 U NA NA NA NA NA NA NA NA
0.019 U 0.0048 U 0.0047 U 0.0047 U 0.0051 U NA NA NA NA NA NA NA NA
0.152 0.0205 0.0201 0.02 0.0219 NA NA NA NA NA NA NA NA
7,910 3,520 4,690 2,880 6,340 NA NA NA NA NA NA NA NA
2 J 7 J 2.1 J 5.9 J 20 NA NA NA NA NA NA NA NA
26.4 91.9 35.6 65.6 105 NA NA NA NA NA NA NA NA
2.5 U 0.58 U 0.55 U 0.66 U 1.1 J NA NA NA NA NA NA NA NA
3.7 U 1.2 U 1.1 U 1.3 U 1.1 U NA NA NA NA NA NA NA NA
1,020 8,890 4,610 14,500 3,080 NA NA NA NA NA NA NA NA
15.1 11.4 11.3 168 12.6 NA NA NA NA NA NA NA NA
6.2 5.5 5.9 4.1 24.4 NA NA NA NA NA NA NA NA
17.5 79 14.2 153 45.3 NA NA NA NA NA NA NA NA
14,500 11,100 11,100 8,430 10,100 NA NA NA NA NA NA NA NA
11.8 305 14.5 177 81.8 NA NA NA NA NA NA NA NA
2,620 2,780 3,420 1,470 1,910 NA NA NA NA NA NA NA NA
85.7 140 212 93.2 76.6 NA NA NA NA NA NA NA NA
0.028 J 0.65 0.18 1.6 2.7 NA NA NA NA NA NA NA NA
19.4 19 19.5 14.6 75.5 NA NA NA NA NA NA NA NA
819 602 771 412 738 NA NA NA NA NA NA NA NA
19.7 U 1.9 U 1.7 U 2.1 U 1.8 U NA NA NA NA NA NA NA NA
3.7 U 0.37 U 0.35 U 0.43 U 0.36 U NA NA NA NA NA NA NA NA
97.8 J 156 136 105 B 164 NA NA NA NA NA NA NA NA
21.7 15.8 30.6 12 23 NA NA NA NA NA NA NA NA
59.2 131 30.8 132 997 NA NA NA NA NA NA NA NA
NA NA NA NA NA NA NA NA NA NA NA NA NA
P.W. Grosser Consulting. Inc / P.W. Grosser Consulting Engineer &
Hydrogeologist, PC
\\Langan.com\data\EP\data5\100287501\Engineering Data\Environmental\Reports\2013�07 � OER Phase II RIWP REVISED (363 Bond�400 Carroll)\Tables\Table 5 � Historical Soil Data for 400 Carroll�OVERALL TABLE
7/9/20133:41 PM
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TABLE 5HISTORICAL SOIL ANALYTICAL RESULTS
Proposed Bond Street Development
400 Carroll Street
Brooklyn, New York
Consultant:
Sample ID: SUBPART 375#6 (Revised Brownfields)
Laboratory Sample Number:
Sampling Date: Unrestricted # Restricted # Restricted # Restricted #
Sampling Depth (ft): Residential Residential Commercial Industrial
Units: (mg/kg) (mg/kg) (mg/kg) (mg/kg) (mg/kg)
VOCs
1,1,1�Trichloroethane 71�55�6 0.68 100 100 500 1,0001,1�Dichloroethane 75�34�3 0.27 19 26 240 4801,1�Dichloroethene 75�35�4 0.33 100 100 500 1,0001,2�Dichloroethane 107�06�2 0.02 2.3 3.1 30 60
1,2�Dichloroethene (cis) 156�59�2 0.25 59 100 500 1,0001,2�Dichloroethene (trans) 156�60�5 0.19 100 100 500 1,000
1,2,3�Trichlorobenzene 87�61�6 ��� ��� ��� ��� ���
1,2,3�Trichloropropane 96�18�4 ��� ��� ��� ��� ���1,2,4�Trichlorobenzene 120�82�1 ��� ��� ��� ��� ���1,2,4�Trimethylbenzene 95�63�6 3.6 47 52 190 380
1,3,5�Trimethylbenzene 108�67�8 8.4 47 52 190 380
4�Isopropyltoluene 99�87�6 ��� ��� ��� ��� ���
Acetone 67�64�1 0.05 100 100 500 1,000
Benzene 71�43�2 0.06 2.9 4.8 44 89
n�Butylbenzene 104�51�8 12 100 100 500 1,000
Carbon Disulfide 75�15�0 ��� ��� ��� ��� ���
Carbon tetrachloride 56�23�5 0.76 1.4 2.4 22 44
Chlorobenzene 108�90�7 1.1 100 100 500 1,000
Chloroform 67�66�3 0.37 10.00 49 350 700Diethylbenzene�p 105�05�5 ��� ��� ��� ��� ���
Ethylbenzene 100�41�4 1 30 41 390 780
p�Ethyltoluene 622�96�8 ��� ��� ��� ��� ���
Isopropyl Benzene 98�82�8 ��� ��� ��� ��� ���p�Isopropyltoluene 99�87�6 ��� ��� ��� ��� ���
Methyl ethyl ketone (MEK / 2�butanone) 78�93�3 0.12 100 100 500 1,000
Methylene chloride 75�09�2 0.05 51 100 500 1,000
4�Methyl�2�Pentanone 108�10�1 ��� ��� ��� ��� ���Naphthalene 91�20�3 ��� ��� ��� ��� ���
Propylbenzene�n 103�65�1 3.9 100 100 500 1,000
Sec�Butylbenzene 135�98�8 11 100 100 500 1,000Tert�Butylbezene 98�06�6 5.9 100 100 500 1,000
Tetrachloroethene 127�18�4 1.3 5.5 19 150 300
Toluene 108�88�3 0.7 100 100 500 1,000
Trichloroethene 79�01�6 0.47 10 21 200 400Tetramethylbenzene�1,2,4,5 95�93�2 ��� ��� ��� ��� ���
Vinyl Chloride 75�01�4 0.02 0.21 0.9 13 27
1,2�Xylene (o�Xylene) 95�47�6 0.26 100 100 500 1,000
1,3�Xylene (m�Xylene) 108�38�3 0.26 100 100 500 1,000Xylene (m,p�Xylene) 108�38�3 0.26 100 100 500 1,000
Xylene (total) 1330�20�7 0.26 100 100 500 1,000
SVOCs
1,2�Dichlorobenzene 95�50�1 1.1 100 100 500 1,000
1,2�Diphenylhydrazine 122�66�7 ��� ��� ��� ��� ���
1,2,4�Trichlorobenzene 120�82�1 ��� ��� ��� ��� ���
2�Methylnaphthalene 91�57�6 ��� ��� ��� ��� ���
2�Nitrophenol 88�75�5 ��� ��� ��� ��� ���
2,4�Dimethylphenol 105�67�9 ��� ��� ��� ��� ���
2,6�Dinitrotoluene 606�20�2 ��� ��� ��� ��� ���
3�Nitroanaline 99�09�2 ��� ��� ��� ��� ���
4�Chloroanaline 106�47�8 ��� ��� ��� ��� ���
4�Nitroaniline 100�01�6 ��� ��� ��� ��� ���
Acenaphthene 83�32�9 20 100 100 500 1,000
Acenaphthylene 208�96�8 100 100 100 500 1,000
Anthracene 120�12�7 100 100 100 500 1,000
Benzo (a) anthracene 56�55�3 1 1 1 5.6 11
Benzo (a) pyrene 50�32�8 1 1 1 1 1.1
Benzo (b) fluoranthene 205�99�2 1 1 1 5.6 11
Benzo (g,h,i) perylene 191�24�2 100 100 100 500 1,000
Benzo (k) fluoranthene 207�08�9 0.8 1 3.9 56 110
Benzyl alcohol 100�51�6 ��� ��� ��� ��� ���
bis(2�chloroethoxy)methane 111�91�1 ��� ��� ��� ��� ���
bis(2�ethylhexyl)phthalate 117�81�7 ��� ��� ��� ��� ���
Butylbenzylphthalate 85�68�7 ��� ��� ��� ��� ���
Carbozole 86�74�8 ��� ��� ��� ��� ���
Chrysene 218�01�9 1 1 3.9 56 110
Dibenzo (a,h) anthracene 53�70�3 0.33 0.33 0.33 0.56 1.1
Dibenzofuran 132�64�9 ��� ��� ��� ��� ���
Fluoranthene 206�44�0 100 100 100 500 1,000
Fluorene 86�73�7 30 100 100 500 1,000
Hexachloroethane 67�72�1 ��� ��� ��� ��� ���
Indeno (1,2,3�cd) pyrene 193�39�5 0.5 0.5 0.5 5.6 11
Isophorone 78�59�1 ��� ��� ��� ��� ���
n�Nitrosodiphenylamine 86�30�6 ��� ��� ��� ��� ����
Naphthalene 91�20�3 12 100 100 500 1,000
Nitrobenzene 98�95�3 ��� ��� ��� ��� ���
o�Cresol(s) (2�Methylphenol) 95�48�7 0.33 100.00 100 500 1,000
m,p�Cresol(s) (3&4�Methylphenol) 106�44�5 0.33 34 100 500 1,000
p�Cresol(s) (4�Methylphenol) 106�44�5 0.33 34 100 500 1,000
Pentachlorophenol 87�86�5 0.8 2.4 6.7 6.7 55
Phenanthrene 85�01�8 100 100 100 500 1,000
Phenol 108�95�2 0.33 100 100 500 1,000
Pyrene 129�00�0 100 100 100 500 1,000
TPH # Diesel Range Organics
Fuel Oil #2 ��� ��� ��� ��� ���
Total DRO TPH ��� ��� ��� ��� ���
Unknown DRO TPH ��� ��� ��� ��� ���
PCBs/Pesticides
Aroclor 1242 53469�21�9 0.1 1 1 1 25
Aroclor 1248 12672�29�6 0.1 1 1 1 25
Aroclor 1260 11096�82�5 0.1 1 1 1 25
Total PCBs/Pesticides ��� ��� ��� ��� ��� ���
Metals
Aluminum 7429�90�5 ��� ��� ��� ��� ���
Arsenic 7440�38�2 13 16 16 16 16
Barium 7440�39�3 350 350 400 400 10,000
Beryllium 7440�41�7 7.2 14 72 590 2,700
Cadmium 7440�43�9 2.5 2.5 4.3 9.3 60
Calcium 7440�70�2 ��� ��� ��� ��� ���
Chromium 7440�47�3
Cobalt 7440�48�4 ��� ��� ��� ��� ���
Copper 7440�50�8 50 270 270 270 10,000
Iron 7439�89�6 ��� ��� ��� ��� ���
Lead 7439�92�1 63 400 400 1,000 3,900
Magnesium 7439�95�4 ��� ��� ��� ��� ���
Manganese 7439�96�5 1600 2,000 2,000 10,000 10,000
Mercury (elemental) 7439�97�6 0.18 0.81 0.81 2.8 5.7
Nickel 7440�02�0 30 140 310 310 10,000
Potassium 7440�09�7 ��� ��� ��� ��� ���
Selenium 7782�49�2 3.9 36 180 1,500 6,800
Silver 7440�22�4 2 36 180 1,500 6,800
Sodium 7440�23�5 ��� ��� ��� ��� ���
Vanadium 7440�62�2 ��� ��� ��� ��� ���
Zinc 7440�66�6 109 2200 10000 10000 10000
Miscellaneous
Percent Solid (%) ��� ��� ��� ��� ��� ���
NOTES:
NYSDEC Soil Cleanup Objective Tables can be found in Tables 375�6.8(a) and 375�6.8(b) dated 14 December 2006.
Sample data for ELM, Cosmos, and Tradewind were provided in the Phase II Investigation Report, 400 Carroll Street by ELM dated May 2005.
Sample data for PW Grosser were provided in the PW Grosser Draft Subsurface Investigation Summary Report dated 16 June 2011.
Sample data for Zeb Environmental were provided in an environmental investigatiton provided by Sive Padget & Riesel, LLP.
Italicized values indicate method detection limit (MDL) exceeds criteria.
Cosmos Environmental Services Samples:
^ : EcoTest Laboratories reported that it could not separate the isonomers for benzo(b)fluoranthene and benzo(k)fluoranthene. Therefore, the sum is split evenly between the two analytes.
1: Elevated detection limits due to interference in sample.
2: Sample was a composite of TP�1, TP�3, TP�6, and TP�8.
Qualifiers:
E:Concentration of analyte exceeds the range of the calibration curve and/or linear range of the instrument.
J:Estimated value. This represents an estimated concentration for Tentatively Identified Compounds (TICs).
U:The analytical results is not detected above the Methof Detection Limit (MDL). All MDLs are lower than the lowest calibration standard concentration.
ND:Not detected at the reporting limit (RL) for the sample.
CAS No.UNRESTRICTE
D USE
Protection of Public Health
P�12 P�1B P�1B P�2 P�2 P�3 P�3 P�4 P�4 P�5 P�5 P�6 P�6 P�7
1204165�5 1204166�1 1204166�2 1204166�3 1204166�4 1204166�5 1204166�6 1204166�7 1204166�8 1204166�9 1204166�10 1204166�11 1204166�12 1204166�13
4/12/2012 4/11/2012 4/11/2012 4/11/2012 4/11/2012 4/11/2012 4/11/2012 4/11/2012 4/11/2012 4/11/2012 4/11/2012 4/11/2012 4/11/2012 4/11/20124�5 4�5 6�7 4�5 6�7 3.5�5 7�7.5 3.5�5 6�7 3.5�5 7�7.5 4�5 6.5�7 4�5
mg/kg Q mg/kg Q mg/kg Q mg/kg Q mg/kg Q mg/kg Q mg/kg Q mg/kg Q mg/kg Q mg/kg Q mg/kg Q mg/kg Q mg/kg Q mg/kg Q
0.0801 U 0.0889 U 0.079 U 0.0105 U 0.00486 U 0.258 U 0.0114 U 0.164 U 0.0101 U 0.0136 U 0.232 U 0.0837 U 0.00206 U 0.178 U0.0462 U 0.0513 U 0.0456 U 0.00925 U 0.00427 U 0.149 U 0.01 U 0.0945 U 0.00891 U 0.012 U 0.134 U 0.0483 U 0.00181 U 0.103 U0.057 U 0.0633 U 0.0562 U 0.0109 U 0.00505 U 0.184 U 0.0119 U 0.117 U 0.0105 U 0.0142 U 0.165 U 0.0596 U 0.00214 U 0.127 U0.077 U 0.0855 U 0.076 U 0.0116 U 0.00537 U 0.248 U 0.0126 U 0.158 U 0.0112 U 0.0151 U 0.224 U 0.0805 U 0.00227 U 0.172 U
0.0647 U 0.0718 U 0.0638 U 0.0107 U 0.00494 U 0.209 U 0.0116 U 0.132 U 0.0103 U 0.0139 U 0.188 U 0.0676 U 0.00209 U 0.144 U0.0416 U 0.0462 U 0.041 U 0.0105 U 0.00486 U 0.134 U 0.0114 U 0.0851 U 0.0101 U 0.0136 U 0.121 U 0.0435 U 0.00206 U 0.0926 U
0.0554 U 0.221 J 0.157 J 0.0102 U 0.0047 U 0.179 U 0.011 U 0.113 U 0.0098 U 0.0132 U 0.161 U 0.058 U 0.00199 U 0.123 U
0.494 J 0.504 J 0.0821 U 0.0104 U 0.00481 U 1.71 J 0.0113 U 0.17 U 0.01 U 0.0135 U 1.2 J 0.0869 U 0.00203 U 0.97 J0.0693 U 0.146 J 0.0684 U 0.0108 U 0.00497 U 0.224 U 0.0117 U 0.142 U 0.0104 U 0.0139 U 0.201 U 0.0724 U 0.0021 U 0.154 U0.116 J 0.0752 U 0.0669 U 0.0126 U 0.00582 U 0.219 U 0.0137 U 0.401 J 0.0121 U 0.0163 U 0.197 U 0.159 J 0.00246 U 3.08
0.0662 U 0.0735 U 0.0654 U 0.0125 U 0.00577 U 0.214 U 0.0135 U 0.135 U 0.012 U 0.0162 U 0.192 U 0.0692 U 0.00244 U 1.36 J
0.126 J 0.0581 U 0.0517 U 0.0124 U 0.00574 U 0.169 U 0.0135 U 1.01 J 0.012 U 0.0161 U 0.152 U 0.0547 U 0.00243 U 0.219 J
0.45 U 0.499 U 0.444 U 0.039 U 0.0321 J 1.45 U 0.0423 U 0.92 U 0.0376 U 0.42 1.31 U 0.47 U 0.00763 U 1 U
0.0942 J 0.0735 U 0.0654 U 0.0108 U 0.00499 U 0.214 U 0.0117 U 0.135 U 0.0104 U 0.0376 0.192 U 0.0692 U 0.00211 U 0.378 J
0.549 J 0.703 J 0.472 J 0.0203 J 0.00574 U 0.95 J 0.0135 U 0.32 J 0.012 U 0.23 0.98 J 0.0692 U 0.00243 U 1.09 J
0.0616 U 0.0684 U 0.0608 U 0.00757 U 0.0035 U 0.199 U 0.0369 0.126 U 0.0073 U 0.0567 0.179 U 0.0644 U 0.00148 U 0.137 U
0.0678 U 0.0752 U 0.0669 U 0.0105 U 0.00483 U 0.219 U 0.0113 U 0.139 U 0.0101 U 0.0136 U 0.197 U 0.0708 U 0.00205 U 0.151 U
0.0739 U 0.0821 U 0.073 U 0.0124 U 0.00571 U 0.239 U 0.0134 U 0.151 U 0.0119 U 0.016 U 0.215 U 0.0773 U 0.00242 U 0.165 U
0.0708 U 0.0787 U 0.0699 U 0.0117 U 0.00539 U 0.229 U 0.0127 U 0.145 U 0.0113 U 0.0151 U 0.206 U 0.0741 U 0.00228 U 0.158 U0.818 0.0667 U 0.0593 U 0.0114 U 0.00529 U 0.194 U 0.0124 U 0.123 U 0.011 U 0.111 0.906 J 0.0628 U 0.00224 U 0.781 J
0.238 J 0.0701 U 0.0623 U 0.0102 U 0.00473 U 0.204 U 0.0111 U 0.129 U 0.00986 U 0.0133 U 0.183 U 0.066 U 0.002 U 1.98
0.371 J 0.0667 U 0.0593 U 0.0124 U 0.00571 U 0.194 U 0.0134 U 0.222 J 0.0119 U 0.042 0.174 U 0.0628 U 0.00242 U 1.39 J
0.492 J 0.298 J 0.0669 U 0.0123 U 0.00566 U 0.31 J 0.0133 U 0.139 U 0.0118 U 0.0159 U 0.357 J 0.0708 U 0.0024 U 0.674 J0.126 J 0.0581 U 0.0517 U 0.0124 U 0.00574 U 0.169 U 0.0135 U 1.01 J 0.012 U 0.0161 U 0.152 U 0.0547 U 0.00243 U 0.219 J
0.296 U 0.328 U 0.292 U 0.021 U 0.00969 U 0.954 U 0.0305 J 0.605 U 0.0202 U 0.0272 U 0.858 U 0.309 U 0.0041 U 0.659 U
0.0601 U 0.0667 U 0.0593 U 0.0109 U 0.00502 U 0.194 U 0.0118 U 0.123 U 0.0545 0.132 0.174 U 0.0628 U 0.00212 U 0.134 U
0.28 U 0.311 U 0.277 U 0.0281 U 0.013 U 0.905 U 0.0305 U 0.573 U 0.0271 U 0.0364 U 0.814 U 0.293 U 0.00549 U 0.624 U0.845 0.0564 U 0.0502 U 0.00803 U 0.0227 0 0.164 U 0.00872 U 0.73 J 0.0461 0.0104 U 0.148 U 0.0531 U 0.00157 U 69.7
0.71 J 0.271 J 0.0623 U 0.0113 U 0.00521 U 0.471 J 0.0122 U 0.129 U 0.0109 U 0.193 0.834 J 0.066 U 0.0022 U 0.92 J
0.814 0.802 J 0.427 J 0.0126 U 0.00582 U 0.179 U 0.0137 U 0.113 U 0.0121 U 0.0163 U 0.161 U 0.058 U 0.00246 U 1.56 J0.27 J 0.285 J 0.156 J 0.0358 0.00555 U 0.995 J 0.013 U 0.139 U 0.0116 U 0.131 0.4 J 0.0708 U 0.00235 U 0.438 J
0.0909 U 0.101 U 0.0897 U 0.0124 U 0.00571 U 0.293 U 0.0134 U 0.186 U 0.0247 J 0.035 J 0.264 U 0.095 U 0.00242 U 0.202 U
0.0693 U 0.0769 U 0.0684 U 0.0129 J 0.00507 U 0.224 U 0.0119 U 0.142 U 0.0106 U 0.0164 J 0.201 U 0.0724 U 0.00215 U 0.973 J
0.0708 U 0.0787 U 0.0699 U 0.0101 U 0.00465 U 0.229 U 0.0109 U 0.145 U 0.00969 U 0.013 U 0.206 U 0.0741 U 0.00197 U 0.158 U3.11 3.17 1.97 0.109 0.0148 2.92 0.0383 1.66 0.0312 0.95 4.91 0.112 J 0.00623 4.91
0.0662 U 0.0735 U 0.0654 U 0.0127 U 0.00587 U 0.214 U 0.0138 U 0.135 U 0.0123 U 0.0165 U 0.192 U 0.0692 U 0.00249 U 0.147 U
0.057 U 0.0633 U 0.0562 U 0.0127 U 0.00585 U 0.184 U 0.0137 U 0.117 U 0.0122 U 0.0164 U 0.165 U 0.0596 U 0.00247 U 1.11 J
0.148 J 0.147 U 0.131 U 0.0242 U 0.0112 U 0.427 U 0.0262 U 0.271 U 0.0233 U 0.0313 U 0.384 U 0.138 U 0.00472 U 2.9 J0.148 J 0.147 U 0.131 U 0.0242 U 0.0112 U 0.427 U 0.0262 U 0.271 U 0.0233 U 0.0313 U 0.384 U 0.138 U 0.00472 U 2.9 J
NA NA NA NA NA NA NA NA NA NA NA NA NA NA
0.0381 U 0.0423 U 0.0375 U 0.0357 U 0.0413 U 0.0409 U 0.0387 U 0.0389 U 0.0344 U 0.0463 U 0.0553 U 0.0398 U 0.0349 U 0.0424 U
0.0373 U 0.0413 U 0.0367 U 0.0349 U 0.0403 U 0.122 J 0.0378 U 0.038 U 0.0337 U 0.0452 U 0.054 U 0.0389 U 0.0341 U 0.0415 U
0.0514 U 0.171 J 0.0505 U 0.0481 U 0.0555 U 0.244 J 0.0521 U 0.0524 U 0.0464 U 0.0623 U 0.0744 U 0.0535 U 0.047 U 0.0571 U
0.491 J 0.0543 U 0.0482 U 0.0459 U 0.053 U 1.67 0.0497 U 1.03 0 0.0443 U 0.0594 U 0.071 U 0.0511 U 0.0448 U 4.39 0
0.0375 U 0.0416 U 0.0369 U 0.0351 U 0.0406 U 0.0403 U 0.0381 U 0.0383 U 0.0339 U 0.0455 U 0.0544 U 0.299 J 0.0343 U 0.0418 U
0.211 J 0.412 J 0.0507 U 0.0483 U 0.0558 U 1.43 0.0524 U 0.436 J 0.0466 U 0.412 J 0.202 J 0.0538 U 0.0472 U 0.308 J
0.0509 U 0.94 0.199 J 0.0476 U 0.055 U 0.0546 U 0.0516 U 0.0519 U 0.0459 U 0.0617 U 0.2 J 0.053 U 0.0465 U 0.0566 U
0.2 J 0.293 J 0.107 J 0.0199 U 0.023 U 0.0228 U 0.0216 U 0.0217 U 0.0192 U 0.213 J 0.179 J 0.0888 J 0.0194 U 0.552 J
0.047 U 0.702 0.0462 U 0.044 U 0.0509 U 0.0505 U 0.0477 U 0.549 J 0.0425 U 0.457 J 0.243 J 0.0708 J 0.043 U 0.0523 U
0.121 U 0.342 J 0.119 U 0.113 U 0.131 U 0.69 0.123 U 0.361 J 0.109 U 0.146 U 0.175 U 0.126 U 0.11 U 0.134 U
2.95 1.01 0.17 J 0.145 J 0.0562 U 3.62 0.0528 U 0.802 0 0.0469 U 0.681 J 0.211 J 0.0542 U 0.0475 U 6.75
0.0425 U 0.0471 U 0.0417 U 0.0398 U 0.0459 U 0.0456 U 0.0431 U 0.0433 U 0.0384 U 0.0515 U 0.0615 U 0.0443 U 0.0388 U 0.0473 U
2.13 0.0609 U 0.054 U 0.257 J 0.0594 U 0.0589 U 0.0558 U 0.056 U 0.0496 U 0.0666 U 0.0796 U 0.0573 U 0.0502 U 1.18
1.83 0.538 J 0.0513 U 1.04 0.15 J 11.3 E 0.053 U 1.36 0.0472 U 0.412 J 0.0757 U 0.0544 U 0.0477 U 1.13
1.46 0.865 0.0632 U 1.09 0.18 J 14.6 E 0.0653 U 1.15 0.0581 U 0.452 J 0.0932 U 0.0671 U 0.0588 U 0.757
1.11 0.592 J 0.0504 U 0.873 0.139 J 10.4 0.052 U 1.01 0.0463 U 0.352 J 0.0742 U 0.0534 U 0.0468 U 0.587 J
1.29 0.886 0.0927 U 0.709 0.102 U 7.56 0.0957 U 1.06 0.0852 U 0.458 J 0.137 U 0.0983 U 0.0862 U 0.743
1.14 0.601 J 0.0924 U 0.906 0.167 J 11.9 E 0.0954 U 1.04 0.0848 U 0.365 J 0.136 U 0.0979 U 0.0859 U 0.637 J
0.0728 U 0.0807 U 0.0716 U 0.0682 U 0.0788 U 0.0781 U 0.0739 U 0.0743 U 0.0658 U 0.0883 U 0.106 U 0.0759 U 0.0666 U 0.0907 J
0.0511 U 0.0566 U 0.0502 U 0.0479 U 0.0553 U 0.0548 U 0.0519 U 0.0521 U 0.0462 U 0.062 U 0.0741 U 0.0533 U 0.0467 U 0.0569 U
3.31 0.0896 U 0.0795 U 0.0757 U 0.0874 U 0.0868 U 0.0821 U 0.0825 U 0.073 U 0.139 J 0.117 U 0.0843 U 0.0739 U 0.092 J
0.0652 U 0.0722 U 0.0641 U 0.061 U 0.0705 U 0.0699 U 0.0662 U 0.0665 U 0.0589 U 0.079 U 0.0945 U 0.068 U 0.0596 U 0.0725 U
0.0711 U 0.0788 U 0.0699 U 0.0936 J 0.0769 U 0.0763 U 0.0722 U 0.0725 U 0.0642 U 0.0862 U 0.103 U 0.0741 U 0.065 U 0.514 J
1.96 0.554 J 0.0642 U 1.06 0.17 J 10.5 0.0663 U 1.4 0.059 U 0.437 J 0.0946 U 0.0681 U 0.0597 U 1.01
0.0689 U 0.0763 U 0.0677 U 0.0645 U 0.0745 U 3.87 0.0699 U 0.0703 U 0.0622 U 0.0835 U 0.0998 U 0.0718 U 0.063 U 0.0766 U
1.39 0.0457 U 0.0405 U 0.0386 U 0.0446 U 0.0442 U 0.0419 U 0.0421 U 0.0372 U 0.05 U 0.37 J 0.043 U 0.0377 U 3.83
7.63 0.952 0.0983 J 2.04 0.174 J 12.1 E 0.069 U 3.02 0.0614 U 0.984 0.157 J 0.0709 U 0.0622 U 8.06
3.16 0.055 U 0.0488 U 0.096 J 0.0537 U 4.36 0.0504 U 0.0506 U 0.0448 U 0.581 J 0.553 J 0.0517 U 0.0454 U 4.12
0.0549 U 0.0609 U 0.054 U 0.0514 U 0.0594 U 0.0589 U 0.0558 U 0.056 U 0.0496 U 1.62 0 0.0796 U 0.0573 U 0.0502 U 0.0611 U
0.915 0.744 0.0561 U 0.644 0.0801 J 0.0612 U 0.0579 U 0.78 0.0515 U 0.323 J 0.0826 U 0.0595 U 0.0521 U 0.496 J
0.0564 U 0.0625 U 0.0555 U 0.0528 U 0.061 U 0.0605 U 0.0573 U 0.0576 U 0.0509 U 0.0684 U 0.0818 U 0.0875 J 0.0516 U 0.0628 U
0.0673 U 0.0746 U 0.0661 U 0.063 U 0.0728 U 0.0722 U 0.0683 U 0.0686 U 0.0608 U 0.0816 U 0.0975 U 0.0701 U 0.0615 U 0.452 J
1.9 0.055 U 0.0488 U 0.0465 U 0.0537 U 0.0532 U 0.0504 U 0.533 J 0.0448 U 0.0602 U 0.0719 U 0.0517 U 0.0454 U 4.32
0.0478 U 0.0529 U 0.047 U 0.0447 U 0.0517 U 0.0513 U 0.0485 U 0.0487 U 0.0431 U 0.202 J 0.0692 U 0.0498 U 0.0437 U 0.229 J
0.0442 U 0.049 U 0.0434 U 0.0414 U 0.0478 U 0.0474 U 0.0449 U 0.0451 U 0.0399 U 0.0536 U 0.064 U 0.0461 U 0.0404 U 0.0492 U
0.0381 U 0.0423 U 0.0375 U 0.0357 U 0.0413 U 0.282 0.0387 U 0.0389 U 0.0344 U 0.0913 0.0553 U 0.0398 U 0.0349 U 0.0424 U
0.0381 U 0.0423 U 0.0375 U 0.0357 U 0.0413 U 0.282 0.0387 U 0.0389 U 0.0344 U 0.0913 0.0553 U 0.0398 U 0.0349 U 0.0424 U
0.468 U 0.518 U 0.46 U 0.438 U 0.506 U 0.502 U 0.475 U 0.477 U 0.423 U 0.567 U 0.678 U 0.488 U 0.428 U 0.521 U
8.63 2 0.0552 U 1.05 0.0607 U 0.0603 U 0.057 U 3.46 0.0507 U 0.0681 U 0.447 J 0.0586 U 0.0514 U 12.3 E
0.0322 U 0.0357 U 0.0317 U 0.0302 U 0.0348 U 0.0346 U 0.0327 U 0.0329 U 0.0291 U 0.0391 U 0.0467 U 0.0336 U 0.0295 U 0.0359 U
7.16 1.19 0.135 J 1.78 0.18 J 13 E 0.0464 U 3.91 0.0412 U 1.14 0.25 J 0.0476 U 0.0418 U 5.43
NA NA NA NA NA NA NA NA NA NA NA NA NA NA
NA NA NA NA NA NA NA NA NA NA NA NA NA NA
NA NA NA NA NA NA NA NA NA NA NA NA NA NA
NA NA NA NA NA NA NA NA NA NA NA NA NA NA
NA NA NA NA NA NA NA NA NA NA NA NA NA NA
NA NA NA NA NA NA NA NA NA NA NA NA NA NA
NA NA NA NA NA NA NA NA NA NA NA NA NA NA
NA NA NA NA NA NA NA NA NA NA NA NA NA NA
NA NA NA NA NA NA NA NA NA NA NA NA NA NA
NA NA NA NA NA NA NA NA NA NA NA NA NA NA
NA NA NA NA NA NA NA NA NA NA NA NA NA NA
NA NA NA NA NA NA NA NA NA NA NA NA NA NA
NA NA NA NA NA NA NA NA NA NA NA NA NA NA
NA NA NA NA NA NA NA NA NA NA NA NA NA NA
NA NA NA NA NA NA NA NA NA NA NA NA NA NA
NA NA NA NA NA NA NA NA NA NA NA NA NA NA
NA NA NA NA NA NA NA NA NA NA NA NA NA NA
NA NA NA NA NA NA NA NA NA NA NA NA NA NA
NA NA NA NA NA NA NA NA NA NA NA NA NA NA
NA NA NA NA NA NA NA NA NA NA NA NA NA NA
NA NA NA NA NA NA NA NA NA NA NA NA NA NA
NA NA NA NA NA NA NA NA NA NA NA NA NA NA
NA NA NA NA NA NA NA NA NA NA NA NA NA NA
NA NA NA NA NA NA NA NA NA NA NA NA NA NA
NA NA NA NA NA NA NA NA NA NA NA NA NA NA
NA NA NA NA NA NA NA NA NA NA NA NA NA NA
NA NA NA NA NA NA NA NA NA NA NA NA NA NA
NA NA NA NA NA NA NA NA NA NA NA NA NA NA
NA NA NA NA NA NA NA NA NA NA NA NA NA NA
Zeb Environmental
\\Langan.com\data\EP\data5\100287501\Engineering Data\Environmental\Reports\2013�07 � OER Phase II RIWP REVISED (363 Bond�400 Carroll)\Tables\Table 5 � Historical Soil Data for 400 Carroll�OVERALL TABLE
7/9/20133:41 PM
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TABLE 5HISTORICAL SOIL ANALYTICAL RESULTS
Proposed Bond Street Development
400 Carroll Street
Brooklyn, New York
Consultant:
Sample ID: SUBPART 375#6 (Revised Brownfields)
Laboratory Sample Number:
Sampling Date: Unrestricted # Restricted # Restricted # Restricted #
Sampling Depth (ft): Residential Residential Commercial Industrial
Units: (mg/kg) (mg/kg) (mg/kg) (mg/kg) (mg/kg)
VOCs
1,1,1�Trichloroethane 71�55�6 0.68 100 100 500 1,0001,1�Dichloroethane 75�34�3 0.27 19 26 240 4801,1�Dichloroethene 75�35�4 0.33 100 100 500 1,0001,2�Dichloroethane 107�06�2 0.02 2.3 3.1 30 60
1,2�Dichloroethene (cis) 156�59�2 0.25 59 100 500 1,0001,2�Dichloroethene (trans) 156�60�5 0.19 100 100 500 1,000
1,2,3�Trichlorobenzene 87�61�6 ��� ��� ��� ��� ���
1,2,3�Trichloropropane 96�18�4 ��� ��� ��� ��� ���1,2,4�Trichlorobenzene 120�82�1 ��� ��� ��� ��� ���1,2,4�Trimethylbenzene 95�63�6 3.6 47 52 190 380
1,3,5�Trimethylbenzene 108�67�8 8.4 47 52 190 380
4�Isopropyltoluene 99�87�6 ��� ��� ��� ��� ���
Acetone 67�64�1 0.05 100 100 500 1,000
Benzene 71�43�2 0.06 2.9 4.8 44 89
n�Butylbenzene 104�51�8 12 100 100 500 1,000
Carbon Disulfide 75�15�0 ��� ��� ��� ��� ���
Carbon tetrachloride 56�23�5 0.76 1.4 2.4 22 44
Chlorobenzene 108�90�7 1.1 100 100 500 1,000
Chloroform 67�66�3 0.37 10.00 49 350 700Diethylbenzene�p 105�05�5 ��� ��� ��� ��� ���
Ethylbenzene 100�41�4 1 30 41 390 780
p�Ethyltoluene 622�96�8 ��� ��� ��� ��� ���
Isopropyl Benzene 98�82�8 ��� ��� ��� ��� ���p�Isopropyltoluene 99�87�6 ��� ��� ��� ��� ���
Methyl ethyl ketone (MEK / 2�butanone) 78�93�3 0.12 100 100 500 1,000
Methylene chloride 75�09�2 0.05 51 100 500 1,000
4�Methyl�2�Pentanone 108�10�1 ��� ��� ��� ��� ���Naphthalene 91�20�3 ��� ��� ��� ��� ���
Propylbenzene�n 103�65�1 3.9 100 100 500 1,000
Sec�Butylbenzene 135�98�8 11 100 100 500 1,000Tert�Butylbezene 98�06�6 5.9 100 100 500 1,000
Tetrachloroethene 127�18�4 1.3 5.5 19 150 300
Toluene 108�88�3 0.7 100 100 500 1,000
Trichloroethene 79�01�6 0.47 10 21 200 400Tetramethylbenzene�1,2,4,5 95�93�2 ��� ��� ��� ��� ���
Vinyl Chloride 75�01�4 0.02 0.21 0.9 13 27
1,2�Xylene (o�Xylene) 95�47�6 0.26 100 100 500 1,000
1,3�Xylene (m�Xylene) 108�38�3 0.26 100 100 500 1,000Xylene (m,p�Xylene) 108�38�3 0.26 100 100 500 1,000
Xylene (total) 1330�20�7 0.26 100 100 500 1,000
SVOCs
1,2�Dichlorobenzene 95�50�1 1.1 100 100 500 1,000
1,2�Diphenylhydrazine 122�66�7 ��� ��� ��� ��� ���
1,2,4�Trichlorobenzene 120�82�1 ��� ��� ��� ��� ���
2�Methylnaphthalene 91�57�6 ��� ��� ��� ��� ���
2�Nitrophenol 88�75�5 ��� ��� ��� ��� ���
2,4�Dimethylphenol 105�67�9 ��� ��� ��� ��� ���
2,6�Dinitrotoluene 606�20�2 ��� ��� ��� ��� ���
3�Nitroanaline 99�09�2 ��� ��� ��� ��� ���
4�Chloroanaline 106�47�8 ��� ��� ��� ��� ���
4�Nitroaniline 100�01�6 ��� ��� ��� ��� ���
Acenaphthene 83�32�9 20 100 100 500 1,000
Acenaphthylene 208�96�8 100 100 100 500 1,000
Anthracene 120�12�7 100 100 100 500 1,000
Benzo (a) anthracene 56�55�3 1 1 1 5.6 11
Benzo (a) pyrene 50�32�8 1 1 1 1 1.1
Benzo (b) fluoranthene 205�99�2 1 1 1 5.6 11
Benzo (g,h,i) perylene 191�24�2 100 100 100 500 1,000
Benzo (k) fluoranthene 207�08�9 0.8 1 3.9 56 110
Benzyl alcohol 100�51�6 ��� ��� ��� ��� ���
bis(2�chloroethoxy)methane 111�91�1 ��� ��� ��� ��� ���
bis(2�ethylhexyl)phthalate 117�81�7 ��� ��� ��� ��� ���
Butylbenzylphthalate 85�68�7 ��� ��� ��� ��� ���
Carbozole 86�74�8 ��� ��� ��� ��� ���
Chrysene 218�01�9 1 1 3.9 56 110
Dibenzo (a,h) anthracene 53�70�3 0.33 0.33 0.33 0.56 1.1
Dibenzofuran 132�64�9 ��� ��� ��� ��� ���
Fluoranthene 206�44�0 100 100 100 500 1,000
Fluorene 86�73�7 30 100 100 500 1,000
Hexachloroethane 67�72�1 ��� ��� ��� ��� ���
Indeno (1,2,3�cd) pyrene 193�39�5 0.5 0.5 0.5 5.6 11
Isophorone 78�59�1 ��� ��� ��� ��� ���
n�Nitrosodiphenylamine 86�30�6 ��� ��� ��� ��� ����
Naphthalene 91�20�3 12 100 100 500 1,000
Nitrobenzene 98�95�3 ��� ��� ��� ��� ���
o�Cresol(s) (2�Methylphenol) 95�48�7 0.33 100.00 100 500 1,000
m,p�Cresol(s) (3&4�Methylphenol) 106�44�5 0.33 34 100 500 1,000
p�Cresol(s) (4�Methylphenol) 106�44�5 0.33 34 100 500 1,000
Pentachlorophenol 87�86�5 0.8 2.4 6.7 6.7 55
Phenanthrene 85�01�8 100 100 100 500 1,000
Phenol 108�95�2 0.33 100 100 500 1,000
Pyrene 129�00�0 100 100 100 500 1,000
TPH # Diesel Range Organics
Fuel Oil #2 ��� ��� ��� ��� ���
Total DRO TPH ��� ��� ��� ��� ���
Unknown DRO TPH ��� ��� ��� ��� ���
PCBs/Pesticides
Aroclor 1242 53469�21�9 0.1 1 1 1 25
Aroclor 1248 12672�29�6 0.1 1 1 1 25
Aroclor 1260 11096�82�5 0.1 1 1 1 25
Total PCBs/Pesticides ��� ��� ��� ��� ��� ���
Metals
Aluminum 7429�90�5 ��� ��� ��� ��� ���
Arsenic 7440�38�2 13 16 16 16 16
Barium 7440�39�3 350 350 400 400 10,000
Beryllium 7440�41�7 7.2 14 72 590 2,700
Cadmium 7440�43�9 2.5 2.5 4.3 9.3 60
Calcium 7440�70�2 ��� ��� ��� ��� ���
Chromium 7440�47�3
Cobalt 7440�48�4 ��� ��� ��� ��� ���
Copper 7440�50�8 50 270 270 270 10,000
Iron 7439�89�6 ��� ��� ��� ��� ���
Lead 7439�92�1 63 400 400 1,000 3,900
Magnesium 7439�95�4 ��� ��� ��� ��� ���
Manganese 7439�96�5 1600 2,000 2,000 10,000 10,000
Mercury (elemental) 7439�97�6 0.18 0.81 0.81 2.8 5.7
Nickel 7440�02�0 30 140 310 310 10,000
Potassium 7440�09�7 ��� ��� ��� ��� ���
Selenium 7782�49�2 3.9 36 180 1,500 6,800
Silver 7440�22�4 2 36 180 1,500 6,800
Sodium 7440�23�5 ��� ��� ��� ��� ���
Vanadium 7440�62�2 ��� ��� ��� ��� ���
Zinc 7440�66�6 109 2200 10000 10000 10000
Miscellaneous
Percent Solid (%) ��� ��� ��� ��� ��� ���
NOTES:
NYSDEC Soil Cleanup Objective Tables can be found in Tables 375�6.8(a) and 375�6.8(b) dated 14 December 2006.
Sample data for ELM, Cosmos, and Tradewind were provided in the Phase II Investigation Report, 400 Carroll Street by ELM dated May 2005.
Sample data for PW Grosser were provided in the PW Grosser Draft Subsurface Investigation Summary Report dated 16 June 2011.
Sample data for Zeb Environmental were provided in an environmental investigatiton provided by Sive Padget & Riesel, LLP.
Italicized values indicate method detection limit (MDL) exceeds criteria.
Cosmos Environmental Services Samples:
^ : EcoTest Laboratories reported that it could not separate the isonomers for benzo(b)fluoranthene and benzo(k)fluoranthene. Therefore, the sum is split evenly between the two analytes.
1: Elevated detection limits due to interference in sample.
2: Sample was a composite of TP�1, TP�3, TP�6, and TP�8.
Qualifiers:
E:Concentration of analyte exceeds the range of the calibration curve and/or linear range of the instrument.
J:Estimated value. This represents an estimated concentration for Tentatively Identified Compounds (TICs).
U:The analytical results is not detected above the Methof Detection Limit (MDL). All MDLs are lower than the lowest calibration standard concentration.
ND:Not detected at the reporting limit (RL) for the sample.
CAS No.UNRESTRICTE
D USE
Protection of Public Health
P�7 P�8 P�8 TP�1 TP�3 TP�61
TP�71
TP�8 Composite2
NE Corner NW Corner SE Corner SW Corner
1204166�14 1204166�15 1204166�16 C974508/1 C974508/2 C974508/3 C974508/4 C974508/5 C974508/7
4/11/2012 4/11/2012 4/11/2012 10/26/1997 10/26/1997 10/26/1997 10/26/1997 10/26/1997 10/26/1997 9/20/2002 9/20/2002 9/20/2002 9/20/20027�7.5 4�5 7�7.5
mg/kg Q mg/kg Q mg/kg Q mg/kg Q mg/kg Q mg/kg Q mg/kg Q mg/kg Q mg/kg Q mg/kg Q mg/kg Q mg/kg Q mg/kg Q
0.00206 U 0.108 U 0.0107 U NA NA NA NA NA NA 0.005 U 0.005 U 0.005 U 0.005 U0.00181 U 0.0621 U 0.00938 U NA NA NA NA NA NA 0.005 U 0.005 U 0.005 U 0.005 U0.00214 U 0.0766 U 0.0111 U NA NA NA NA NA NA 0.005 U 0.005 U 0.005 U 0.005 U0.00227 U 0.104 U 0.0118 U NA NA NA NA NA NA 0.005 U 0.005 U 0.005 U 0.005 U0.00209 U 0.374 J 0.0108 U NA NA NA NA NA NA 0.005 U 0.005 U 0.005 U 0.005 U0.00206 U 0.0559 U 0.0107 U NA NA NA NA NA NA 0.005 U 0.005 U 0.005 U 0.005 U
0.00199 U 0.0745 U 0.0103 U NA NA NA NA NA NA 0.005 U 0.005 U 0.005 U 0.005 U
0.00203 U 0.112 U 0.0105 U NA NA NA NA NA NA 0.005 U 0.005 U 0.005 U 0.005 U0.0021 U 0.0932 U 0.0109 U NA NA NA NA NA NA 0.005 U 0.005 U 0.005 U 0.005 U0.00246 U 0.161 J 0.0128 U 1.1 0.055 0.11 0.14 0.25 NA 0.005 U 0.005 U 0.005 U 0.005 U
0.00244 U 0.089 U 0.0127 U 0.29 0.15 0.07 0.065 0.12 NA 0.005 U 0.005 U 0.005 U 0.005 U
0.00243 U 0.0704 U 0.0126 U NA NA NA NA NA NA 0.005 U 0.005 U 0.005 U 0.0092
0.00763 U 0.604 U 0.0396 U NA NA NA NA NA NA NA NA NA NA
0.00211 U 0.388 J 0.011 U 1.1 0.27 0.2 0.15 1.3 NA 0.005 U 0.005 U 0.005 U 0.005 U
0.00243 U 1.53 0.0126 U 4.3 1.1 1.9 1 0.99 NA 0.005 U 0.005 U 0.005 U 0.005 U
0.00148 U 0.0828 U 0.00768 U NA NA NA NA NA NA 0.005 U 0.005 U 0.005 U 0.005 U
0.00205 U 0.0911 U 0.0106 U NA NA NA NA NA NA 0.005 U 0.005 U 0.005 U 0.005 U
0.00242 U 0.0994 U 0.0125 U NA NA NA NA NA NA 0.005 U 0.005 U 0.005 U 0.005 U
0.00228 U 0.0952 U 0.0118 U NA NA NA NA NA NA 0.005 U 0.005 U 0.005 U 0.005 U0.00224 U 2.71 0.0116 U NA NA NA NA NA NA NA NA NA NA
0.002 U 0.0849 U 0.0104 U 1.2 0.095 0.12 0.05 0.36 NA 0.005 U 0.005 U 0.005 U 0.005 U
0.00242 U 0.15 J 0.0125 U NA NA NA NA NA NA NA NA NA NA
0.0024 U 0.916 J 0.0124 U 4.2 1.2 0.49 0.52 1.1 NA 0.005 U 0.005 U 0.005 U 0.005 U0.00243 U 0.0704 U 0.0126 U 0.22 0.07 0.06 0.05 0.61 NA NA NA NA NA
0.00495 J 0.397 U 0.0213 U NA NA NA NA NA NA NA NA NA NA
0.0105 0.0807 U 0.083 NA NA NA NA NA NA 0.005 U 0.005 U 0.005 U 0.005 U
0.00549 U 0.377 U 0.0285 U NA NA NA NA NA NA NA NA NA NA0.0112 1.98 0.00815 U 2.1 0.38 0.29 0.31 0.35 NA 0.005 U 0.005 U 0.005 U 0.005 U
0.0022 U 1.71 0.0114 U 8.4 2 0.31 0.84 1.4 NA 0.005 U 0.005 U 0.005 U 0.005 U
0.00246 U 2.07 0.0128 U 5.8 1.1 2.8 0.89 1.1 NA 0.005 U 0.005 U 0.005 U 0.005 U0.00235 U 0.656 J 0.0122 U 2.5 0.47 1.2 0.39 0.88 NA 0.0091 0.005 U 0.005 U 0.0054
0.00455 J 0.122 U 0.0342 NA NA NA NA NA NA 0.005 U 0.005 U 0.005 U 0.005 U
0.00215 U 0.188 J 0.0111 U 0.76 0.11 0.19 0.13 0.28 NA 0.005 U 0.005 U 0.005 U 0.005 U
0.00197 U 0.0952 U 0.0102 U NA NA NA NA NA NA 0.005 U 0.005 U 0.005 U 0.005 U0.00672 6.27 0.0366 NA NA NA NA NA NA NA NA NA NA
0.00249 U 0.089 U 0.0129 U NA NA NA NA NA NA 0.005 U 0.005 U 0.005 U 0.005 U
0.00247 U 0.0766 U 0.0128 U 0.28 0.05 U 0.06 0.065 0.085 NA 0.005 U 0.005 U 0.005 U 0.005 U
0.00472 U 0.328 J 0.0245 U NA NA NA NA NA NA NA NA NA NA0.00472 U 0.328 J 0.0245 U 2.4 0.27 0.35 0.29 0.65 NA 0.01 U 0.01 U 0.01 U 0.01 U
NA NA NA 2.7 0.31 0.41 0.35 0.73 NA NA NA NA NA
0.035 U 0.0512 U 0.0362 U NA NA NA NA NA NA NA NA NA NA
0.0342 U 0.05 U 0.0354 U NA NA NA NA NA NA NA NA NA NA
0.0471 U 0.0689 U 0.0488 U NA NA NA NA NA NA NA NA NA NA
0.045 U 0.0657 U 0.0465 U NA NA NA NA NA NA NA NA NA NA
0.0344 U 0.0503 U 0.0356 U NA NA NA NA NA NA NA NA NA NA
0.0473 U 0.142 J 0.049 U NA NA NA NA NA NA NA NA NA NA
0.0467 U 0.0682 U 0.0483 U NA NA NA NA NA NA NA NA NA NA
0.0195 U 0.18 J 0.0202 U NA NA NA NA NA NA NA NA NA NA
0.0431 U 0.0631 U 0.0447 U NA NA NA NA NA NA NA NA NA NA
0.111 U 0.162 U 0.115 U NA NA NA NA NA NA NA NA NA NA
0.0477 U 0.364 J 0.0494 U 1.9 6.5 0.3 U 0.3 U 5.6 NA 0.17 0.3 0.33 0.46
0.039 U 0.639 J 0.0403 U NA NA NA NA NA NA 0.094 0.27 0.19 0.3
0.0504 U 0.924 0.0522 U 1.5 2.1 0.3 U 0.3 U 3.9 NA 0.25 0.61 0.37 1.3
0.0479 U 2.56 0.0496 U 2.4 1.1 0.3 U 0.3 U 4.3 NA 0.77 1.2 1.2 2.7
0.059 U 5.57 0.0611 U 2.8 1.5 0.3 U 0.3 U 3.7 NA 0.88 1.5 1.2 2.5
0.047 U 2.33 0.0487 U 2.4 ^ 0.95 ^ 0.3 U 0.3 U 3.3 ^ NA 1 1.8 1.5 3.2
0.0865 U 5.78 0.0896 U 1.1 0.6 0.3 U 0.3 U 1.3 NA 0.65 1.2 0.83 1.9
0.0862 U 2.98 0.0892 U 2.4 ^ 0.95 ^ 0.3 U 0.3 U 3.3 ^ NA 0.42 0.75 0.68 1.6
0.0668 U 0.0977 U 0.0692 U NA NA NA NA NA NA NA NA NA NA
0.0469 U 0.0685 U 0.0485 U NA NA NA NA NA NA NA NA NA NA
0.0742 U 0.108 U 0.0768 U NA NA NA NA NA NA NA NA NA NA
0.0598 U 0.0874 U 0.0619 U NA NA NA NA NA NA NA NA NA NA
0.0652 U 0.0954 U 0.0675 U NA NA NA NA NA NA NA NA NA NA
0.0599 U 2.56 0.062 U 2.4 1.3 0.3 0.3 U 4.2 NA 0.88 1.4 1.3 2.9
0.0632 U 0.0924 U 0.0654 U 0.48 0.3 U 0.3 U 0.3 U 0.71 NA 0.19 0.33 0.25 0.58
0.0378 U 0.0553 U 0.0392 U NA NA NA NA NA NA NA NA NA NA
0.0624 U 4.57 0.0646 U 4.3 2.6 0.62 0.35 9.2 NA 1.6 2.7 2.8 6.3
0.0455 U 0.384 J 0.0471 U 1.7 3.9 2 0.3 U 4 NA 1.1 0.29 0.33 0.55
0.0504 U 0.22 J 0.0522 U NA NA NA NA NA NA NA NA NA NA
0.0523 U 3.16 0.0542 U 1.1 0.36 0.3 U 0.3 U 1.2 NA 0.54 1 0.73 1.7
0.0518 U 0.0757 U 0.0536 U NA NA NA NA NA NA NA NA NA NA
0.0617 U 0.0902 U 0.0639 U NA NA NA NA NA NA NA NA NA NA
0.0455 U 0.381 J 0.0471 U 0.3 U 7.8 0.3 U 0.3 U 0.3 U NA 0.08 U 0.19 0.17 0.44
0.0438 U 0.0641 U 0.0454 U NA NA NA NA NA NA NA NA NA NA
0.0405 U 0.0593 U 0.042 U NA NA NA NA NA NA NA NA NA NA
0.035 U 0.0512 U 0.0362 U NA NA NA NA NA NA NA NA NA NA
0.035 U 0.0512 U 0.0362 U NA NA NA NA NA NA NA NA NA NA
0.429 U 0.627 U 0.444 U NA NA NA NA NA NA NA NA NA NA
0.0515 U 0.947 0 0.0533 U 5.4 7.1 1.7 0.3 U 22 NA 0.81 2.3 0.93 5.6
0.0296 U 0.0432 U 0.0306 U NA NA NA NA NA NA NA NA NA NA
0.0419 U 7.27 0.0434 U 6.2 5.7 1.3 0.86 13 NA 1.4 2.3 2.2 4.3
NA NA NA NA NA NA NA NA NA NA NA NA 270
NA NA NA NA NA NA NA NA NA NA NA NA 490
NA NA NA NA NA NA NA NA NA NA NA NA 220
NA NA NA NA NA NA NA NA NA NA NA NA NA
NA NA NA NA NA NA NA NA NA NA NA NA NA
NA NA NA NA NA NA NA NA NA NA NA NA NA
NA NA NA NA NA NA NA NA NA NA NA NA NA
NA NA NA NA NA NA NA NA NA NA NA NA NA
NA NA NA NA NA NA NA NA 1.4 NA NA NA NA
NA NA NA NA NA NA NA NA 28 NA NA NA NA
NA NA NA NA NA NA NA NA NA NA NA NA NA
NA NA NA NA NA NA NA NA 0.1 U NA NA NA NA
NA NA NA NA NA NA NA NA NA NA NA NA NA
NA NA NA NA NA NA NA NA 2.8 NA NA NA NA
NA NA NA NA NA NA NA NA NA NA NA NA NA
NA NA NA NA NA NA NA NA NA NA NA NA NA
NA NA NA NA NA NA NA NA NA NA NA NA NA
NA NA NA NA NA NA NA NA 6.6 NA NA NA NA
NA NA NA NA NA NA NA NA NA NA NA NA NA
NA NA NA NA NA NA NA NA NA NA NA NA NA
NA NA NA NA NA NA NA NA 2.6 NA NA NA NA
NA NA NA NA NA NA NA NA NA NA NA NA NA
NA NA NA NA NA NA NA NA NA NA NA NA NA
NA NA NA NA NA NA NA NA 0.96 NA NA NA NA
NA NA NA NA NA NA NA NA 0.2 U NA NA NA NA
NA NA NA NA NA NA NA NA NA NA NA NA NA
NA NA NA NA NA NA NA NA NA NA NA NA NA
NA NA NA NA NA NA NA NA NA NA NA NA NA
NA NA NA 71 67 68 78 82 NA NA NA NA NA
Cosmos Environmental Tradewinds
0209069�02A/B 0209069�03A/B 0209069�04A/B 0209069�05A/B
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TABLE 6
SUMMARY OF HISTORICAL GROUNDWATER ANALYTICAL RESULTS
PROPOSED BOND STREET DEVELOPMENT
400 Carroll Street
Brooklyn, New York
Tradewind
Sample ID: MW�1 SB�2/TW SB�3/W SB�6/TW SB�7/TW SB�11/TW SB�12/TW PPW�3 W1
Laboratory Sample Number: 207936�006 207935�013 207935�014 207935�015 207935�016 207935�017 207935�018 C974508/6 0209069�01A
Sampling Date: Part 703*** 10/25/2004 10/27/2004 10/27/2004 10/27/2004 10/27/2004 10/27/2004 10/27/2004 10/26/1997 9/20/2002
Units: (ug/L) ug/l Q ug/l Q ug/l Q ug/l Q ug/l Q ug/l Q ug/l Q ug/l Q ug/l Q
VOCs
1,1,1�Trichloroethane 71�55�6 5 0.9 U 5 U 5 U 5 U 5 U 5 U 5 U NA NA
1,1�Dichloroethane 75�34�3 5 0.4 U 5 U 5 U 5 U 5 U 5 U 5 U 1 U 1 U
1,1�Dichloroethene 75�35�4 5 0.8 U 5 U 5 U 5 U 5 U 5 U 5 U 1 U 1 U
1,1,1�Trichloroethane 71�55�6 5 0.8 U 5 U 5 U 5 U 5 U 5 U 5 U 1 U 1 U
1,1,2�Trichloroethane 79�00�5 1 0.8 U 5 U 5 U 5 U 5 U 5 U 5 U 1 U 1 U
1,1,2,2�Tetrachloroethane 79�34�5 5 0.7 U 5 U 5 U 5 U 5 U 5 U 5 U 1 U 1 U
1,2�Dichloroethane 107�06�2 0.6 0.6 U 5 U 5 U 5 U 5 U 5 U 5 U 1 U 1 U
1,2�Dichloroethene (cis) 156�59�2 5 0.7 U 5 U 5 U 5 U 5 U 5 U 5 U NA 1 U
1,2�Dichloroethene (trans) 156�60�5 5 0.5 U 5 U 5 U 5 U 5 U 5 U 5 U 1 U 1 U
1,2,4�Trimethylbenzene 95�63�6 5 NA NA NA NA NA NA NA NA 5.3
Acetone 67�64�1 5 10 6.6 J 13 8.4 J 7.4 J 9.6 J 4.3 J NA 1 U
Benzene 71�43�2 1 3.2 J 8.8 1.7 J 1 J 5 U 33 0.63 J 52 7.4
Bromomethane 74�83�9 5 2.7 U 5 U 5 U 5 U 5 U 5 U 5 U 1 U 1 U
Carbon Disulfide 75�15�0 5* 0.4 U 5 U 5 U 5 U 5 U 1 J 5 U NA 1 U
Carbon tetrachloride 56�23�5 5 0.6 U 5 U 5 U 5 U 5 U 5 U 5 U 1 U 1 U
Chlorobenzene 108�90�7 5 0.5 U 5 U 5 U 5 U 5 U 5 U 5 U 1 U 1 U
Chloroethane 75�00�3 5* 1.7 U 5 U 5 U 5 U 5 U 5 U 5 U 1 U 1 U
Chloroform 67�66�3 7 0.6 U 5 U 5 U 5 U 5 U 2.8 J 0.82 J 1 U 1 U
Ethylbenzene 100�41�4 5 0.5 U 5 U 5 U 5 U 5 U 3.7 J 5 U 1 1 U
Isopropyl Benzene 98�82�8 5 NA NA NA NA NA NA NA NA 12
Methyl ethyl ketone (MEK / 2�butanone) 78�93�3 5 1.6 U 10 U 10 U 10 U 10 U 10 U 10 U NA NA
Methylene chloride 75�09�2 5 0.6 UB 5 UB 5 UB 5 UB 5 UB 5 UB 5 UB 1 U 1 U
4�Methyl�2�Pentanone 108�10�1 5* 0.9 U 10 U 10 U 10 U 10 U 10 U 10 U NA NA
Propylbenzene�n 103�65�1 5 NA NA NA NA NA NA NA NA 7.9
Sec�Butylbenzene 135�98�8 5 NA NA NA NA NA NA NA NA 17
Styrene 100�42�5 5 0.7 U 5 U 5 U 5 U 5 U 5 U 5 U NA 1 U
Tert�Butylbezene 98�06�6 5 NA NA NA NA NA NA NA NA 6.7
Tetrachloroethene 127�18�4 5* 0.4 U 5 U 5 U 5 U 5 U 5 U 5 U 1 U 1 U
Toluene 108�88�3 5 0.57 J 1 J 5 U 5 U 5 U 5.5 5 U 3 1 U
Trichloroethene 79�01�6 5 0.8 U 5 U 5 U 5 U 5 U 5 U 5 U 1 U 1 U
Vinyl Chloride 75�01�4 2 0.6 U 5 U 5 U 5 U 5 U 5 U 5 U 1 U 1 U
1,2�Xylene (o�Xylene) 95�47�6 5 NA NA NA NA NA NA NA 2 1 U
m&p�Xylene NA NA NA NA NA NA NA 6 2 U
Xylene (mixed) 1330�20�7 5 0.9 U 1 J 5 U 5 U 1 J 17 5 U NA NA
SVOCs
1,2,4�Trichlorobenzene 120�82�1 5 0.6 U 10 U 10 U 10 U 10 U 20 U 10 U NA NA
2�Chlorophenol 95�57�8 5* 1 U 10 U 10 U 10 U 10 U 20 U 10 U NA NA
2�Methylnaphthalene 91�57�6 5* 0.6 U 10 U 10 U 10 U 10 U 1 J 10 U NA NA
2�Nitroaniline 88�74�4 5* 0.9 U 50 U 50 U 50 U 50 U 100 U 50 U NA NA
2�Nitrophenol 88�75�5 5* 1 U 10 U 10 U 10 U 10 U 20 U 10 U NA NA
2,4�Dichlorophenol 120�83�2 5* 1 U 10 U 10 U 10 U 10 U 20 U 10 U NA NA
2,4�Dimethylphenol 105�67�9 5* 0.8 U 10 U 10 U 10 U 10 U 20 U 10 U NA NA
2,4�Dinitrophenol 51�28�5 5* 2 U 50 U 50 U 50 U 50 U 100 U 50 U NA NA
2,4�Dinitrotoluene 121�14�2 5 1 U 10 U 10 U 10 U 10 U 20 U 10 U NA NA
2,4,5�Trichlorophenol 95�95�4 5* 0.9 U 50 U 50 U 50 U 50 U 100 U 50 U NA NA
2,6�Dinitrotoluene 606�20�2 5 0.6 U 10 U 10 U 10 U 10 U 20 U 10 U NA NA
3�Nitroaniline 99�09�2 5* 0.7 U 50 U 50 U 50 U 50 U 100 U 50 U NA NA
3,3'�Dichlorobenzidine 91�94�1 5 0.7 U 20 U 20 U 20 U 20 U 40 U 20 U NA NA
4�Chloroaniline 106�47�8 5 0.6 U 10 U 10 U 10 U 10 U 20 U 10 U NA NA
4�Chloro�3�methylphenol 35421�08�0 5* 1 U 10 U 10 U 10 U 10 U 20 U 10 U NA NA
4�Nitroaniline 100�01�6 5* 0.8 U 20 U 20 U 20 U 20 U 40 U 20 U NA NA
4�Nitrophenol 100�02�7 5* 0.8 U 50 U 50 U 50 U 50 U 100 U 50 U NA NA
Acenaphthene 83�32�9 20 0.7 U 2 J 1 J 3 J 9 J 89 0.7 J NA NA
Acenaphthylene 208�96�8 5* 0.7 U 10 U 10 U 10 U 10 U 20 U 10 U NA NA
Anthracene 120�12�7 5* 0.8 U 10 U 10 U 10 U 1 J 5 J 10 U NA NA
Benzo(a)anthracene 56�55�3 5* 0.4 U 10 U 10 U 10 U 0.6 J 2 J 10 U NA NA
Benzo(a)pyrene 50�32�8 0.5 U 10 U 10 U 10 U 10 U 2 J 10 U NA NA
Benzo(b)fluoranthene 205�99�2 5* 1 U 10 U 10 U 10 U 10 U 20 U 10 U NA NA
Benzo(g,h,i)perylene 191�24�2 5* 0.6 U 10 U 10 U 10 U 10 U 2 J 10 U NA NA
Benzo(k)fluoranthene 207�08�9 5* 2 U 10 U 10 U 10 U 10 U 20 U 10 U NA NA
bis(2�Chloroethyl)ether 111�44�4 5 0.5 U 10 U 10 U 10 U 10 U 20 U 10 U NA NA
bis(2�Ethylhexyl)phthalate 117�81�7 5* 2 U 10 U 10 U 10 U 10 U 20 U 10 U NA NA
4�Bromophenyl phenyl ether 0.7 U 10 U 10 U 10 U 10 U 20 U 10 U NA NA
Butyl benzyl phthalate 85�68�7 5* 0.6 U 10 U 10 U 10 U 10 U 20 U 10 U NA NA
Carbazole 0.3 U 10 U 10 U 10 U 10 U 20 U 10 U NA NA
4�Chlorophenyl phenyl ether 0.9 U 10 U 10 U 10 U 10 U 20 U 10 U NA NA
Chrysene 218�01�9 5* 0.5 U 10 U 10 U 10 U 10 U 1 J 10 U NA NA
Dibenzo(a,h)anthracene 53�70�3 5* 0.8 U 10 U 10 U 10 U 10 U 20 U 10 U NA NA
Dibenzofuran 132�64�9 7 x 10�7
0.8 U 10 U 0.8 J 10 U 10 U 20 U 10 U NA NA
Diethyl phthalate 84�66�2 5* 0.8 U 10 U 10 U 10 U 10 U 20 U 10 U NA NA
Dimethyl phthalate 131�11�3 5* 0.6 U 10 U 10 U 10 U 10 U 20 U 10 U NA NA
Di�n�octyl phthalate 117�84�0 5* 0.7 U 10 U 10 U 10 U 10 U 20 U 10 U NA NA
Fluoranthene 206�44�0 5* 0.6 U 10 U 10 U 0.8 J 2 J 7 J 10 U NA NA
Fluorene 86�73�7 5* 0.7 U 10 U 1 J ND 4 J 31 10 U NA NA
Hexachlorobenzene 118�74�1 0.04 0.7 U 10 U 10 U 10 U 10 U 20 U 10 U NA NA
Hexachlorobutadiene 87�68�3 0.5 1 U 10 U 10 U 10 U 10 U 20 U 10 U NA NA
Hexachlorocyclopentadiene 77�47�4 5 6 U 10 U 10 U 10 U 10 U 20 U 10 U NA NA
Hexachloroethane 67�72�1 5 0.9 U 10 U 10 U 10 U 10 U 20 U 10 U NA NA
Indeno(1,2,3�cd)pyrene 193�39�5 5* 0.7 U 10 U 10 U 10 U 10 U 20 U 10 U NA NA
Isophorone 78�59�1 5* 0.6 U 10 U 10 U 10 U 10 U 2 J 10 U NA NA
Naphthalene 91�20�3 5* 0.7 U 10 U 10 U 10 U 10 U 10 J 10 U NA NA
Nitrobenzene 98�95�3 0.4 0.5 U 10 U 10 U 10 U 10 U 20 U 10 U NA NA
o�Cresol(s) (2�Methylphenol) 95�48�7 5* 0.9 U 10 U 10 U 10 U 10 U 20 U 10 U NA NA
p�Cresol(s) (4�Methylphenol) 106�44�5 5* 2 U 10 U 10 U 10 U 10 U 20 U 10 U NA NA
Pentachlorophenol 87�86�5 5* 2 U 50 U 50 U 50 U 50 U 100 U 50 U NA NA
Phenanthrene 85�01�8 5* 0.5 U 10 U 10 U 0.7 J 5 J 47 0.5 J NA NA
Phenol 108�95�2 5* 0.5 U 10 U 10 U 10 U 10 U 20 U 10 U NA NA
Pyrene 129�00�0 5* 0.4 U 10 U 10 U 0.9 J 3 J 10 J 10 U NA NA
Oil & Grease ��� NA NA NA NA NA NA NA 63 NA
PCBs
Aroclor 1016 12674�11�2 0.09 0.067 U 0.54 U 0.5 U 0.52 U 0.58 U 0.5 U 0.5 U NA NA
Aroclor 1221 11104�28�2 0.09 0.12 U 1.1 U 1 U 1 U 1.2 U 1 U 1 U NA NA
Aroclor 1232 11141�16�5 0.09 0.095 U 0.54 U 0.5 U 0.52 U 0.58 U 0.5 U 0.5 U NA NA
Aroclor 1242 53469�21�9 0.09 0.085 U 0.54 U 0.5 U 0.52 U 0.58 U 0.5 U 0.5 U NA NA
Aroclor 1248 12672�29�6 0.09 0.071 U 0.54 U 0.5 U 0.52 U 0.58 U 0.5 U 0.5 U NA NA
Aroclor 1254 11097�69�1 0.09 0.11 U 0.54 U 0.5 U 0.52 U 0.58 U 0.5 U 0.5 U NA NA
Aroclor 1260 11096�82�5 0.09 0.12 U 1.1 U 1 U 1 U 0.11 J 1 U 1 U NA NA
Metals
Aluminum 7429�90�5 ��� 114 J 500 U 500 U 500 U 500 U 379 B 500 U NA NA
Antimony 7440�36�0 3 5.4 U 20 U 20 U 8.3 J 20 U 20 U 20 U NA NA
Arsenic 7440�38�2 25 6.7 J 40 U 40 U 9.7 J 40 U 40 U 40 U NA 930
Barium 7440�39�3 1,000 222 101 115 369 287 219 211 NA 8680
Cadmium 7440�43�9 5 1.1 U 10 U 10 U 10 U 10 U 10 U 10 U NA 134
Calcium 7440�70�2 ��� 187,000 174,000 171,000 264,000 233,000 237,000 237,000 NA NA
Cobalt 7440�48�4 5* 1.8 U 10 U 10 U 10 U 10 U 10 U 10 U NA NA
Iron 7439�89�6 300 10,100 80.7 J 426 4,900 3,540 751 1540 NA NA
Lead 7439�92�1 25 6.1 J 10 U 10 U 6.7 J 10 U 4.4 J 10 U NA 109000
Magnesium 7439�95�4 ��� 12,800 28,400 14,700 141,000 32,600 29,200 38,400 NA NA
Manganese 7439�96�5 300 3,870 218 440 621 315 161 344 NA NA
Potassium 7440�09�7 ��� 28,300 26,200 16,100 84,500 23,600 24,500 29,100 NA NA
Selenium 7782�49�2 10 5 U 30 U 30 U 30 U 30 U 30 U 30 U NA 77
Sodium 7440�23�5 20,000 303,000 83,000 20,100 913,000 83,300 57,600 93,400 NA NA
Thallium 7440�28�0 5* 10 U 40 U 40 U 40 U 40 U 40 U 40 U NA NA
Vanadium 7440�62�2 5* 2.3 J 4.3 J 6 U 6 U 6 U 1.6 J 1.5 J NA NA
NOTES:
* : No criteria established, value is generic criteria
***Standards exist for additional criteria not listed in this table
Italicized values indicate method detection limit (MDL) exceeds criteria.
Sample data for ELM, Cosmos, and Tradewind were provided in the Phase II Investigation Report, 400 Carroll Street by ELM dated May 2005.
J: Estimated value
U: Indicates that the result is lower than the MDL.
ELM
NYSDEC Groundwater Criteria are a combination of values from Part 703 if the NYS Code and TAGM 4046. Most values are generic screening values, however where contaminant specific criteria have been established they are used in this table.
CAS No.
Cosmos
Ground Water
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Table 7PROPOSED SAMPLING SUMMARY
Proposed Bond Street Development
Brooklyn, New York
Matrix Sample Depth (ft bgs) Sample Location Rationale Analysis Matrix Sample Depth (ft bgs) Sample Location Rationale Analysis
VOCs
0'bgs - 10' bgs LSB-1 SVOCs
Lead
LSB-2 LSV-11
LSB-3 LSV-12
LSB-4 LSV-13 VOCs
LSV-1 LSV-14
LSV-2 LSV-15
MW-2
MW-5
Matrix Sample Depth (ft bgs) Sample Location Rationale Analysis LMW-9
LMW-10
LSB-22
LSB-23
LSB-24
LSB-10 Horizontal Delineation of AOC-2
LSB-7
LSB-6
LSB-8
LSB-25
LSV-3
LSV-4
LSV-5
LSV-16
LSV-17
LSV-18
LSV-19
LSV-20
LSV-21
LSV-22
MW-1
MW-2
MW-3
--- MW-4
MW-5
LMW-6 And Delineation of LNAPL at AOC-2 & AOC-3
LMW-7 And Delineation of LNAPL at AOC-5
NOTES:
*Subslab and 5' bgs samples will be co-located at each LSV location.
=completed as part of the Phase II Due Diligence Investigation
AOC-1: Proposed Excavation Area - 400 Carroll Street, North
AOC-2: Proposed Excavation Area - 400 Carroll Street, South
AOC-3: Proposed Excavation Area - 363 Bond Street
AOC-5: Former UST Area - 363 Bond Street
VOCs
SVOCs
Pesticides
Site Assessment of Groundwater
400 Carroll StreetFinal Proposed Sampling Summary
VOCs
SVOCs
VOCs
SVOCs
Lead
Groundwater --- Site Assessment of Groundwater
VOCs
SVOCs
Pesticides
PCBs
Total Metals
Filtered Metals
Soil0' bgs - 2' bgs
Groundwater Interface
LSB-21
LSB-27
Site Assessment of Soil and
Horizontal Delineation of AOC-3
VOCs
SVOCs
Pesticides
PCBs
Metals
Soil Vapor 5' bgs Site Assessment of Soil Vapor
Site Assessment of Groundwater
Site Assessment of Soil Vapor VOCs
VOCs
Final Proposed Sampling Summary
Groundwater
VOCs
SVOCs
Pesticides
PCBs
Total Metals
Dissolved Metals
Soil Vapor Subslab
Groundwater ---
363 Bond StreetDue Diligence Sampling Summary
Soil
Horizontal Delineation of
AOC-5
6' bgs - 11' bgs
11' bgs - 15' bgs
Horizontal and Vertical
Delineation of AOC-3
VOCs
SVOCs
Groundwater Interface
Site Assessment of Soil and
Horizontal Delineation of AOC-3
Site Assessment of Soil and
Horizontal Delineation of AOC -5
Site Assessment of Soil VaporSoil Vapor Subslab / 5' bgs*
LSB-5
LSB-9
LSB-22
LSB-23
LSB-24
Soil
0' bgs - 2' bgs
LSB-5
LSB-6
LSB-7
LSB-9
LSB-10Site Assessment of Soil
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Project Drawing Title
KINGS COUNTY NEW YORK
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BLOCK No. 452, LOT Nos. 1 & 15
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Project No.
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10/19/2012
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NEW JERSEY NEW YORK VIRGINIA CALIFORNIA PENNSYLVANIA CONNECTICUT FLORIDA
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AOC-3
AOC-1
AOC-2
AOC-5
SHELVES
RACKS
SEE INSET A
LSV-2
LSV-1
LSB-4LSB-3
LSB-2LSB-1
P-7
P-3
P-2
P-1
P-4
P-9
P-8
P-5
P-6
P-12
P-1BP-1A
P-10
P-11
GP-08
GP-05
GP-10
GP-03GP-04
GP-01GP-11
GP-02 GP-09
GP-06AGP-06B
GP-06C
GP-07C
GP-07AGP-07B
MW-43
MW-36
SB-9
SB-7
SB-4
SB-2
SB-5SB-1
SB-6SB-3
SB-10
SB-11
SB-12
MW-1
SB-8
MW-3
MW-2
MW-5
MW-4
MW-1
SB-5
SB-4
SB-1
SB-3
SB-2
TP-2
TP-5
TP-1
TP-3
TP-4
TP-6
TP-1TP-0
TP-8
TP-3
TP-7
TP-6
TP-4TP-2
.
40 0 40
SCALE IN FEET
Project Drawing Title
KINGS COUNTY NEW YORK
pfqb=mi^k
Project No.
Date
Scale
Drawn By
Last Revised
Figure
100287501
11/6/2012
amf
6/14/2013
1"=40'
River Drive Center 1, 619 River DriveElmwood Park, NJ 07407-1338
T: 201.794.6900 F: 201.794.0366 www.langan.com
mêçéçëÉÇ=_çåÇpíêÉÉí=aÉîÉäçéãÉåí
BLOCK No. 452, LOT Nos. 1 & 15
BROOKLYN
2Langan Engineering & Environmental Services, Inc.
Langan Engineering, Environmental, Surveying andLandscape Architecture, D.P.C.
Langan International LLC
Collectively known as Langan
NJ CERTIFICATE OF AUTHORIZATION No. 24GA27996400
SS
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P-2
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P-4
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GP-08
GP-05
GP-10
GP-03GP-04
GP-01GP-11
GP-02 GP-09
GP-06AGP-06B
GP-06C
GP-07C
GP-07A
GP-07B
MW-43
MW-36
SB-9
MW-1
SB-8
SB-10
SB-11
TP-5
TP-4
TP-8TP-7
Legend
Water Line
Street Extents
Proposed Excavation Area (Langan)
Areas of Concern (AOCs)
Former AST Pipe Ports
Site Boundary
Sample Locations
A Monitoring Well/Piezometer Location (ELM, 2004 - 2005)
Test Pit Location (Zeb Environmental, 2012)"/
Test Pit Location (Cosmo Environmental, 1997)S
Soil Vapor Location (Langan,2012)
Soil Boring Location (Langan, 2012)
!. Soil Boring Location (ELM, 2004 - 2005)
D!. Soil Boring & Temporary Well Location (ELM, 2004 - 2005)
Test Pit Location (ELM, 2004 - 2005)
!. Geoprobe Location (PW Grosser, 2011)
A Monitoring Well Location (PW Grosser, 2011)
Test Pit Location (PW Grosser, 2011)
A
A
Existing Building
Building Features
Former AST Locations
Gowanus Canal
Notes:1. Map features are based on aerial photographs, tax maps, and the following ELM reports: Phase II Investigation Report, 363 Bond Street (May 2005); and Phase II Investigation Report, 400 Carroll Street (May 2005).2. AOC-1: Proposed Excavation Area - 400 Carroll Street, North; AOC-2: Proposed Excavation Area - 400 Carroll Street, South; AOC-3: Proposed Excavation Area - 363 Bond Street; AOC-5: Former UST Area
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ELEVATOROFFICES
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MW-5
MW-4
MW-1
MW-2
AOC-5
SB-5
SB-4
SB-1
LSB-4LSB-3
LSB-2LSB-1
AOC-3
AOC-1
AOC-2
Path: \\Langan.com\data\EP\data5\100287501\ArcGIS\ArcMap_Documents\2012-11 - NYSDEC Phase II RIWP\363 Bond Street-400 Carroll Street (Revised 2013-06-04)\Figure 3 - 363 Bond Data Soil.mxd
.
30 0 30
SCALE IN FEET
Project No.
Date
Scale
Drawn By
Last Revised
002032710
7/2/2012
amf
6/17/2013
1"=30'
River Drive Center 1, 619 River Drive, Elmwood Park, NJ 07407-1338T: 201.794.6900 F: 201.794.0366 www.langan.com
NEW JERSEY NEW YORK VIRGINIA CALIFORNIA
PENNSYLVANIA CONNECTICUT FLORIDA
Project
KINGS COUNTY NEW JERSEY
molmlpba=_lka=
pqobbq=absbilmjbkqBLOCK No. 452, LOT Nos. 1 & 15
BROOKLYN
Drawing Title
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ABU DHABI ATHENS DOHA
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Langan Engineering & Environmental Services, Inc.
Langan Engineering, Environmental, Surveying and Landscape Architecture, D.P.C.
Langan International LLC
Collectively known as Langan
NJ CERTIFICATE OF AUTHORIZATION No. 24GA27996400
SUBPART 375-6 (Revised Brownfields)
Unrestricted Use
Objectives
Protection of Public Health
Residential Restricted
Residential
Restricted
Commercial
Restricted
Industrial
(mg/kg) (mg/kg) (mg/kg) (mg/kg) (mg/kg)
VOCs
1,1�Dichloroethane 0.27 19 26 240 480
1,1�Dichloroethene 0.33 100 100 500 1,000
1,2�Dichloroethane 0.02 2.3 3.1 30 60
1,2�Dichloroethene (cis) 0.25 59 100 500 1,000
1,2�Dichloroethene (trans) 0.19 100 100 500 1,000
Acetone 0.05 100 100 500 1,000
Benzene 0.06 2.9 4.8 44 89
Carbon tetrachloride 0.76 1.4 2.4 22 44
Chloroform 0.37 10 49 350 700
Ethylbenzene 1 30 41 390 780
Methyl ethyl ketone 0.12 100 100 500 1,000
Methylene chloride 0.05 51 100 500 1,000
Toluene 0.7 100 100 500 1,000
Trichloroethene 0.47 10 21 200 400
Vinyl Chloride 0.02 0.21 0.9 13 27
Xylene (total) 0.26 100 100 500 1,000
SVOCs
1,2�Dichlorobenzene 1.1 100 100 500 1,000
Acenaphthene 20 100 100 500 1,000
Anthracene 100 100 100 500 1,000
Benzo (a) anthracene 1 1 1 5.6 11
Benzo (a) pyrene 1 1 1 1 1.1
Benzo (b) fluoranthene 1 1 1 5.60 11
Benzo (g,h,i) perylene 100 100 100 500 1,000
Benzo (k) fluoranthene 0.8 1 3.9 56 110
Chrysene 1 1 3.9 56 110
Dibenzo (a,h) anthracene 0.33 0.33 0.33 0.56 1.1
Fluoranthene 100 100 100 500 1,000
Fluorene 30 100 100 500 1,000
Indeno (1,2,3�cd) pyrene 0.5 0.5 0.5 5.6 11
Naphthalene 12 100 100 500 1,000
o�Cresol(s) (2�Methylphenol) 0.33 100 100 500 1,000
p�Cresol(s) (4�Methylphenol) 0.33 34 100 500 1,000
Pentachlorophenol 0.8 2.4 6.7 6.7 55
Phenanthrene 100 100 100 500 1,000
Phenol 0.33 100 100 500 1,000
Pyrene 100 100 100 500 1,000
PCBs/Pesticides
4,4'�DDE 0.0033 1.8 8.9 62 120
4,4'�DDT 0.0033 1.7 7.9 47 94
4,4'�DDD 0.0033 2.6 13 92 180
Aroclor 1254 0.1 1 1 1 25
Aldrin 0.005 0.019 0.097 0.68 1.4
Dieldrin 0.005 0.039 0.2 1.4 2.8
Polychlorinated biphenyls (PCBs) 0.1 1 1 1 25
Metals
Arsenic 13 16 16 16 16
Barium 350 350 400 400 10,000
Cadmium 2.5 2.5 4.3 9.3 60
Copper 50 270 270 270 10,000
Lead 63 400 400 1,000 3,900
Mercury (elemental) 0.18 0.81 0.81 2.8 5.7
Nickel 30 140 310 310 10,000
Selenium 3.9 36 180 1,500 6,800
Zinc 109 2200 10000 10000 10000
Sample ID: MW�2/1�3
Laboratory Sample Number: 209324�003
Sampling Date: 4/15/2005
Sampling Depth (ft): 1�3'
Units: mg/kg Q
Volatile Organic Compounds
Acetone 0.051 B
Toluene 2.9 J
Semi)Volatile Organic Compounds
1,2�Dichlorobenzene 1.4 U
Benzo (a) anthracene 26
Benzo (a) pyrene 26
Benzo (b) fluoranthene 19
Benzo (k) fluoranthene 19
Chrysene 30
Dibenzo (a,h) anthracene 6.8 J
Indeno (1,2,3�cd) pyrene 15
Naphthalene 23
o�Cresol(s) (2�Methylphenol) 2.2 U
p�Cresol(s) (4�Methylphenol) 4.4 U
Pentachlorophenol 7.1 U
Phenol 2.4 U
PCBs/Pesticides
Dieldrin 0.053
Metals
Arsenic 51.5
Barium 524
Chromium 11.9
Copper 354
Lead 851
Mercury (elemental) 9.9
Zinc 552
Sample ID: MW�2/9�10
Laboratory Sample Number: 209324�004
Sampling Date: 4/15/2005
Sampling Depth (ft): 9�10'
Units: mg/kg Q
Semi)Volatile Organic Compounds
Benzo (a) anthracene 3.7
Benzo (a) pyrene 3.7
Benzo (b) fluoranthene 2.8
Benzo (k) fluoranthene 2.4
Chrysene 4.3
Dibenzo (a,h) anthracene 0.71 J
Indeno (1,2,3�cd) pyrene 1.8
p�Cresol(s) (4�Methylphenol) 0.49 U
Metals
Arsenic 13.9
Chromium 11.4
Copper 69.2
Lead 674
Mercury (elemental) 0.68
Zinc 138
Sample ID: SB�4/9�10.5
Laboratory Sample Number: 209324�017
Sampling Date: 4/21/2005
Sampling Depth (ft): 9�10.5'
Units: mg/kg Q
Volatile Organic Compounds
1,1�Dichloroethane 0.34 U
1,1�Dichloroethene 0.4 U
1,2�Dichloroethane 0.34 U
1,2�Dichloroethene (cis) 0.34 U
1,2�Dichloroethene (trans) 0.28 U
Acetone 0.8 U
Benzene 0.23 U
Chloroform 0.4 U
Ethylbenzene 1.3 J
Methyl ethyl ketone (MEK / 2�
butanone) 0.68 U
Methylene chloride 0.38 JB
Vinyl Chloride 0.46 U
Xylene (total) 5.7
Semi)Volatile Organic Compounds
Benzo (a) anthracene 8.2
Benzo (a) pyrene 7.8
Benzo (b) fluoranthene 4.8 J
Benzo (k) fluoranthene 5.1 J
Chrysene 7.9
Dibenzo (a,h) anthracene 1.4 J
Indeno (1,2,3�cd) pyrene 3.1 J
Naphthalene 20
o�Cresol(s) (2�Methylphenol) 1.6 U
p�Cresol(s) (4�Methylphenol) 3.1 U
Pentachlorophenol 5 U
Phenol 1.7 U
PCBs/Pesticides
4,4'�DDE 0.065
Aroclor 1254 0.88
Aldrin 0.017
Polychlorinated biphenyls 0.88
Metals
Cadmium 32.4
Chromium 10.7
Lead 88.5
Mercury (elemental) 0.46
Zinc 350
Sample ID: SB�4/14�16
Laboratory Sample Number: 209324�018
Sampling Date: 4/21/2005
Sampling Depth (ft): 14�16'
Units: mg/kg Q
PCBs/Pesticides
4,4'�DDE 0.0063
Metals
Chromium 9.5
Location ID
Sample Date
Sample Depth
VOC Sample Depth
Depth Unit
Volatile Organic Compounds
1,4-DIOXANE (P-DIOXANE) < 3.3 U < 3.8 U
ACETONE < 0.093 U < 0.11 U
METHYL ETHYL KETONE (2-BUTANONE) < 0.13 U < 0.15 U
METHYLENE CHLORIDE < 0.070 U < 0.082 U
Semi-Volatile Organic Compounds
BENZO(A)ANTHRACENE 1.58 6.45
BENZO(A)PYRENE 1.41 6.17
BENZO(B)FLUORANTHENE 1.49 4.96
BENZO(K)FLUORANTHENE 0.722 4.51
CHRYSENE 1.55 6.09
DIBENZ(A,H)ANTHRACENE 0.300 1.31
INDENO(1,2,3-C,D)PYRENE 0.762 3.55
LSB-3
8/22/2012
LSB-3
8/22/2012
6-8
6-6.5
ft
12-14
12-12.5
ft
Sample ID: MW�5/7.5�9.5
Laboratory Sample Number: 209324�009
Sampling Date: 4/20/2005
Sampling Depth (ft): 7.5�9.5'
Units: mg/kg Q
Volatile Organic Compounds
1,1�Dichloroethane 0.29 U
1,1�Dichloroethene 0.34 U
1,2�Dichloroethane 0.29 U
1,2�Dichloroethene (cis) 0.29 U
1,2�Dichloroethene (trans) 0.24 U
Acetone 0.68 U
Benzene 0.98 J
Ethylbenzene 1.3 J
Methyl ethyl ketone (MEK / 2�
butanone) 0.58 U
Methylene chloride 0.29 JB
Vinyl Chloride 0.39 U
Xylene (total) 2.4 J
Semi)Volatile Organic Compounds
Acenaphthene 200
Anthracene 270
Benzo (a) anthracene 340
Benzo (a) pyrene 330
Benzo (b) fluoranthene 210
Benzo (g,h,i) perylene 200
Chrysene 410
Dibenzo (a,h) anthracene 84
Fluoranthene 950
Fluorene 200
Indeno (1,2,3�cd) pyrene 170
Naphthalene 300
o�Cresol(s) (2�Methylphenol) 20 U
p�Cresol(s) (4�Methylphenol) 41 U
Pentachlorophenol 66 U
Phenanthrene 1,100
Phenol 22 U
Pyrene 890
PCBs/Pesticides
4,4'�DDE 1.5
4,4'�DDD 0.023 U
4,4'�DDT 0.018 U
Aldrin 0.021 U
Beta�BHC 0.12
Dieldrin 0.019 U
Metals
Arsenic 80.3
Barium 1,060
Chromium 14
Copper 2,680
Lead 1,420
Mercury (elemental) 19.5
Zinc 1,270
Sample ID: MW�5/13�15
Laboratory Sample Number: 209324�010
Sampling Date: 4/20/2005
Sampling Depth (ft): 13�15'
Units: mg/kg Q
Semi)Volatile Organic Compounds
Benzo (a) anthracene 16
Benzo (a) pyrene 14
Benzo (b) fluoranthene 11
Benzo (k) fluoranthene 10
Chrysene 18
Dibenzo (a,h) anthracene 3.9
Indeno (1,2,3�cd) pyrene 7.6
o�Cresol(s) (2�Methylphenol) 0.99 U
p�Cresol(s) (4�Methylphenol) 2 U
Pentachlorophenol 3.2 U
Phenol 1.1 U
PCBs/Pesticides
4,4'�DDE 0.11
Metals
Chromium 4.4
Zinc 1,050
Sample ID: SB�1/1�4
Laboratory Sample Number:
209324�
011
Sampling Date: 4/20/2005
Sampling Depth (ft): 1�4'
Units: mg/kg Q
Volatile Organic Compounds
1,1�Dichloroethane 0.3 U
1,1�Dichloroethene 0.35 U
1,2�Dichloroethane 0.3 U
1,2�Dichloroethene (cis) 0.3
1,2�Dichloroethene (trans) 0.25 U
Acetone 0.71 U
Benzene 0.2 U
Ethylbenzene 1.9 J
Methyl ethyl ketone (MEK / 2�
butanone) 0.61 U
Methylene chloride 0.27 JB
Toluene 0.89 J
Vinyl Chloride 0.41 U
Xylene (total) 3.7
Semi)Volatile Organic Compounds
1,2�Dichlorobenzene 2.8 U
Benzo (a) anthracene 62
Benzo (a) pyrene 61
Benzo (b) fluoranthene 38
Benzo (k) fluoranthene 42
Chrysene 61
Dibenzo (a,h) anthracene 12 J
Fluoranthene 180
Indeno (1,2,3�cd) pyrene 27
Naphthalene 21
o�Cresol(s) (2�Methylphenol) 4.4 U
p�Cresol(s) (4�Methylphenol) 8.8 U
Pentachlorophenol 14 U
Phenanthrene 190
Phenol 4.8 U
Pyrene 110
Metals
Cadmium 4.7
Chromium 12.2
Copper 76.9
Lead 489
Mercury (elemental) 1.5
Zinc 243
Sample ID: SB�1/10�12
Laboratory Sample Number:
209324�
012
Sampling Date: 4/20/2005
Sampling Depth (ft): 10�12'
Units: mg/kg Q
Metals
Chromium 9
Lead 106
Sample ID: MW�4/6�8
Laboratory Sample Number: 209324�007
Sampling Date: 4/20/2005
Sampling Depth (ft): 6�8'
Units: mg/kg Q
Semi)Volatile Organic Compounds
p�Cresol(s) (4�Methylphenol) 0.49 U
Metals
Arsenic 17
Barium 502
Chromium 9.4
Copper 67.7
Lead 1,290
Mercury (elemental) 1.6
Zinc 483
Sample ID: MW�4/12�14
Laboratory Sample Number: 209324�008
Sampling Date: 4/20/2005
Sampling Depth (ft): 12�14'
Units: mg/kg Q
PCBs/Pesticides
4,4'�DDE 0.37
4,4'�DDT 0.11
4,4'�DDD 0.0055 U
Aldrin 0.0052 U
Metals
Chromium 7.1
Lead 201
Mercury (elemental) 0.84
Sample ID: SB�3/6�8
Laboratory Sample Number: 209324�015
Sampling Date: 4/21/2005
Sampling Depth (ft): 6�8'
Units: mg/kg Q
Volatile Organic Compounds
1,1�Dichloroethane 0.38 U
1,1�Dichloroethene 0.44 U
1,2�Dichloroethane 0.38 U
1,2�Dichloroethene (cis) 0.38 U
1,2�Dichloroethene (trans) 0.32 U
Acetone 0.88 U
Benzene 3.1 J
Chloroform 0.44 U
Methyl ethyl ketone (MEK / 2�
butanone) 0.76 U
Methylene chloride 0.32 JB
Toluene 2.7 J
Vinyl Chloride 0.51
Xylene (total) 3.9
Semi)Volatile Organic Compounds
1,2�Dichlorobenzene 1.4 U
Benzo (a) anthracene 22
Benzo (a) pyrene 25
Benzo (b) fluoranthene 15
Benzo (k) fluoranthene 18
Chrysene 27
Dibenzo (a,h) anthracene 4.8 J
Indeno (1,2,3�cd) pyrene 12
o�Cresol(s) (2�Methylphenol) 2.2 U
p�Cresol(s) (4�Methylphenol) 4.4 U
Phenol 2.4
PCBs/Pesticides
4,4'�DDE 0.075
Metals
Copper 78.5
Chromium 8.3
Lead 371
Mercury (elemental) 0.97
Zinc 147
Sample ID: SB�3/10�12
Laboratory Sample Number: 209324�016
Sampling Date: 4/21/2005
Sampling Depth (ft): 10�12'
Units: mg/kg Q
Metals
Chromium 17.1
Nickel 46.2
Zinc 136
Sample ID: SB�2/6�8
Laboratory Sample Number: 209324�013
Sampling Date: 4/20/2005
Sampling Depth (ft): 6�8'
Units: mg/kg Q
Semi)Volatile Organic Compounds
p�Cresol(s) (4�Methylphenol) 0.4 U
Metals
Cadmium 3.4 J
Chromium 2.8 J
Lead 91.9
Selenium 5.5 J
Sample ID: SB�2/10�12
Laboratory Sample Number: 209324�014
Sampling Date: 4/20/2005
Sampling Depth (ft): 10�12'
Units: mg/kg Q
Semi)Volatile Organic Compounds
Benzo (a) anthracene 1.9
Benzo (a) pyrene 2.2
Benzo (b) fluoranthene 1.6
Benzo (k) fluoranthene 1.3
Chrysene 2.2
Dibenzo (a,h) anthracene 0.57 J
Indeno (1,2,3�cd) pyrene 1.1
p�Cresol(s) (4�Methylphenol) 0.56 J
Metals
Chromium 6.8
Lead 1,450
Mercury (elemental) 0.38
Sample ID: MW�1/3�4
Laboratory Sample Number: 209324�001
Sampling Date: 4/15/2005
Sampling Depth (ft): 3�4'
Units: mg/kg Q
Metals
Chromium 22.2
Sample ID: MW�1/9�10
Laboratory Sample Number: 209324�002
Sampling Date: 4/15/2005
Sampling Depth (ft): 9�10'
Units: mg/kg Q
Metals
Chromium 21.2
Location ID
Sample Date
Sample Depth
VOC Sample Depth
Depth Unit
Volatile Organic Compounds
1,4-DIOXANE (P-DIOXANE) < 3.3 U < 4.0 U
ACETONE < 0.094 U < 0.11 U
METHYL ETHYL KETONE (2-BUTANONE) < 0.13 U < 0.16 U
METHYLENE CHLORIDE < 0.071 U < 0.085 U
O-XYLENE (1,2-DIMETHYLBENZENE) 0.218 0.492
M AND P XYLENES 0.437 0.875
Semi-Volatile Organic Compounds
BENZO(A)ANTHRACENE 1.66 0.989
BENZO(A)PYRENE 1.32 0.902
BENZO(B)FLUORANTHENE 1.24 0.754
BENZO(K)FLUORANTHENE 0.864 0.619
CHRYSENE 1.58 1.03
INDENO(1,2,3-C,D)PYRENE 0.718 0.503
8/22/2012
7-9
8.5-9
DUP-1 (LSB-4)
8/22/2012
7
9
ft
LSB-4
8/22/2012
Location ID
Sample Date
Sample Depth
VOC Sample Depth
Depth Unit
Semi-Volatile Organic Compounds
BENZO(A)ANTHRACENE 2.67 2.62
BENZO(A)PYRENE 3.08 2.91
BENZO(B)FLUORANTHENE 3.00 2.84
BENZO(K)FLUORANTHENE 1.36 1.37
CHRYSENE 2.67 2.58
DIBENZ(A,H)ANTHRACENE 0.774 0.686
INDENO(1,2,3-C,D)PYRENE 1.91 1.75
LSB-2
8/21/2012
6.5-8.5
6.5-7
ft
LSB-2
8/21/2012
11.5-13.5
11.5-12
ft
Sample ID: MW�3/4�6
Laboratory Sample Number: 209324�005
Sampling Date: 4/15/2005
Sampling Depth (ft): 4�6'
Units: mg/kg Q
Volatile Organic Compounds
1,1�Dichloroethane 0.71 U
1,1�Dichloroethene 0.83 U
1,2�Dichloroethane 0.71 U
1,2�Dichloroethene (cis) 0.71 U
1,2�Dichloroethene (trans) 0.59 U
Acetone 1.7 U
Benzene 0.47 U
Carbon tetrachloride 1.2 U
Chloroform 0.83 U
Ethylbenzene 1.2 U
Methyl ethyl ketone (MEK / 2�
butanone) 8 B
Methylene chloride 0.47 UB
Trichloroethene 0.83 U
Vinyl Chloride 0.95 U
Xylene (total) 1.2 U
Semi)Volatile Organic Compounds
1,2�Dichlorobenzene 1.3 U
Benzo (a) anthracene 1 U
Benzo (b) fluoranthene 2.1 U
Benzo (k) fluoranthene 0.85 U
Dibenzo (a,h) anthracene 0.85 U
Indeno (1,2,3�cd) pyrene 0.78 U
o�Cresol(s) (2�Methylphenol) 2.1 U
p�Cresol(s) (4�Methylphenol) 4.1 U
Pentachlorophenol 6.6 U
Phenol 2.2 U
Metals
Chromium 9.4
Sample ID: MW�3/13�15
Laboratory Sample Number: 209324�006
Sampling Date: 4/15/2005
Sampling Depth (ft): 13�15'
Units: mg/kg Q
Semi)Volatile Organic Compounds
o�Cresol(s) (2�Methylphenol) 0.41 U
p�Cresol(s) (4�Methylphenol) 0.83 U
Pentachlorophenol 1.3 U
Phenol 0.45 U
Metals
Chromium 9.8
Sample ID: SB�5/7�8
Laboratory Sample Number: 209324�020
Sampling Date: 4/21/2005
Sampling Depth (ft): 7�8'
Units: mg/kg Q
Semi)Volatile Organic Compounds
Benzo (a) anthracene 11
Benzo (a) pyrene 16
Benzo (b) fluoranthene 11
Benzo (k) fluoranthene 10
Chrysene 13
Dibenzo (a,h) anthracene 3.2
Indeno (1,2,3�cd) pyrene 7.6
o�Cresol(s) (2�Methylphenol) 0.79 U
p�Cresol(s) (4�Methylphenol) 1.6 U
Pentachlorophenol 2.6 U
Phenol 0.86 U
Metals
Arsenic 39.2
Chromium 7.8
Copper 176
Lead 582
Mercury (elemental) 2.4
Zinc 520
Sample ID: SB�5/5�7
Laboratory Sample Number: 209324�019
Sampling Date: 4/21/2005
Sampling Depth (ft): 5�7'
Units: mg/kg Q
Metals
Chromium 12.8
Location ID
Sample Date
Sample Depth
VOC Sample Depth
Depth Unit
Volatile Organic Compounds
1,4-DIOXANE (P-DIOXANE) < 3.6 U
ACETONE 0.217 J
ETHYLBENZENE 2.26
METHYL ETHYL KETONE (2-BUTANONE) < 0.15 U
METHYLENE CHLORIDE < 0.078 U
M AND P XYLENES 17.1
Semi-Volatile Organic Compounds
ACENAPHTHENE 72.2
ANTHRACENE 151
BENZO(A)ANTHRACENE 168
BENZO(A)PYRENE 152
BENZO(B)FLUORANTHENE 150
BENZO(K)FLUORANTHENE 76.7
CHRYSENE 166
DIBENZ(A,H)ANTHRACENE 36.9
DIBENZOFURAN 62.1
FLUORANTHENE 473
FLUORENE 84.2
INDENO(1,2,3-C,D)PYRENE 89.9
NAPHTHALENE 102
2-METHYLPHENOL (O-CRESOL) 1.50
PHENANTHRENE 539
PHENOL 1.91
PYRENE 340
Metals
Lead 435
LSB-1
8/21/2012
7.5-9.5
8-8.5
ft
Legend
Site BoundaryFormer BuildingExisting BuildingBuilding FeaturesFormer AST LocationsFormer AST Pipe Ports
Gowanus Canal
A Monitoring Well Location (ELM, 2004 - 2005)
Water Line
Street Extents
!. Soil Boring Location (ELM, 2004 - 2005)
Areas of Concern (AOCs)
Soil Boring Location (ELM, 2004 - 2005) A
Notes:1. Map features are based on aerial photographs, tax maps, and the following ELM reports: Phase II Investigation Report, 363 Bond Street (May 2005), and Phase II Investigation Report, 400 Carroll Street (May 2005).2. All ELM sample locations are approximate and based on the following ELM reports: Phase II Investigation Report, 363 Bond Street (May 2005), and Phase II Investigation Report, 400 Carroll Street (May 2005).3. Italicized values indicate method detection limit exceeds criteria.4. AOC-1: Proposed Excavation Area - 400 Carroll Street, North; AOC-2: Proposed Excavation Area - 400 Carroll Street, South; AOC-3: Proposed Excavation Area - 363 Bond Street; AOC-5: Former UST Area
A
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LOADING BAY
METAL FLOOR
ELEVATOR
MW-3
MW-2
MW-5
MW-4
MW-1
AOC-3
AOC-1
AOC-2
AOC-5
Path: \\Langan.com\data\EP\data5\100287501\ArcGIS\ArcMap_Documents\2012-11 - NYSDEC Phase II RIWP\363 Bond Street-400 Carroll Street (Revised 2013-06)\Figure 4 - 363 Soil Bond Data Groundwater.mxd
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SCALE IN FEET
Project No.
Date
Scale
Drawn By
Last Revised
100287501
7/2/2012
amf
6/21/2013
1"=30'
River Drive Center 1, 619 River Drive, Elmwood Park, NJ 07407-1338T: 201.794.6900 F: 201.794.0366 www.langan.com
NEW JERSEY NEW YORK VIRGINIA CALIFORNIA
PENNSYLVANIA CONNECTICUT FLORIDA
Project
KINGS COUNTY NEW YORK
molmlpba=_lka=
pqobbq=absbilmjbkq
BROOKLYN
Drawing Title
PSP=_lka=pqobbq
prjj^ov=lc=
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^k^ivqf`^i=obpriqp
Figure
4
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ABU DHABI ATHENS DOHA
DUBAI ISTANBUL
Langan Engineering & Environmental Services, Inc.
Langan Engineering, Environmental, Surveying and Landscape Architecture, D.P.C.
Langan International LLC
Collectively known as Langan
NJ CERTIFICATE OF AUTHORIZATION No. 24GA27996400
Sample ID: MW 1
Laboratory Sample Number: 209387 001
Sampling Date: 4/28/2005
Total Dissolved
Units: ug/l Q ug/l Q
Dibenzofuran 0.9 U NA
Hexachlorobenzene 0.7 U NA
Hexachlorobutadiene 1 U NA
Hexachlorocyclopentadiene 6 U NA
Nitrobenzene 0.5 U NA
Aroclor 1221 0.12 U NA
Aroclor 1232 0.094 U NA
Aroclor 1254 0.11 U NA
Aroclor 1260 0.095 U NA
Dieldrin 0.0066 U NA
Toxaphene 0.25 U NA
Polychlorinated biphenyls(PCBs) 0.12 U NA
Antimony 5.4 U 5.4 U
Iron 5,990 1,290
Iron and Manganese 6,946 2,267
Manganese 956 977
Sodium 105,000 111,000
Thallium 10 U 10 U
Sample ID: MW 2
Laboratory Sample Number: 209387 002
Sampling Date: 4/28/2005
Total Dissolved
Units: ug/l Q ug/l Q
2 Methylnaphthalene 6 C NA
Dibenzofuran 3 J NA
Fluorene 6 J NA
Hexachlorobenzene 0.7 U NA
Hexachlorobutadiene 1 U NA
Hexachlorocyclopentadiene 6 U NA
Naphthalene 23 NA
Nitrobenzene 0.5 U NA
Phenanthrene 10 J NA
Aroclor 1221 0.12 U NA
Aroclor 1232 0.09 U NA
Aroclor 1254 0.1 U NA
Aroclor 1260 0.091 U NA
Dieldrin 0.0063 U NA
Toxaphene 0.24 U NA
Polychlorinated biphenyls (PCBs) 0.12 U NA
Antimony 5.4 U 5.4 U
Iron 3,730 54 U
Iron and Manganese 4,274 512
Manganese 544 512
Sodium 155,000 156,000
Thallium 10 U 10 U
Sample ID: MW 4
Laboratory Sample Number: 209387 003
Sampling Date: 4/28/2005
Total Dissolved
Units: ug/l Q ug/l Q
Dibenzofuran 0.9 U NA
Hexachlorobenzene 0.8 U NA
Hexachlorobutadiene 1 U NA
Hexachlorocyclopentadiene 7 U NA
Nitrobenzene 0.6 U NA
Aroclor 1221 0.12 U NA
Aroclor 1254 0.1 U NA
Dieldrin 0.0062 U NA
Toxaphene 0.23 U NA
Polychlorinated biphenyls (PCBs) 0.12 U NA
Antimony 5.4 U 5.4 U
Cadmium 16.4 15.3
Sodium 28,400 29,000
Thallium 10 U 10 U
Vanadium 5.7 J 5.2 J
Sample ID: MW 5
Laboratory Sample Number: 209387 004
Sampling Date: 4/28/2005
Total Dissolved
Units: ug/l Q ug/l Q
1,1,2 Trichloroethane 3 U NA
1,2 Dichloroethane 3 U NA
1,2 Dichloroethene (cis) 450 NA
Acetone 11 J NA
Benzene 59 NA
Bromomethane 6 U NA
Ethylbenzene 19 J NA
Methyl ethyl ketone (MEK / 2
butanone) 21 J NA
Methylene chloride 2.9 JB NA
Toluene 38 NA
Vinyl Chloride 320 NA
Xylene (mixed) 94 NA
1,2,4 Trichlorobenzene 7 U NA
2 Chlorophenol 12 U NA
2 Methylnaphthalene 150 NA
2 Nitroaniline 10 U NA
2 Nitrophenol 13 U NA
2,4 Dichlorophenol 11 U NA
2,4 Dimethylphenol 260 NA
2,4 Dinitrophenol 20 U NA
2,4 Dinitrotoluene 11 U NA
2,4,5 Trichlorophenol 10 U NA
2,6 Dinitrotoluene 7 U NA
3 Nitroaniline 8 U NA
3,3' Dichlorobenzidine 8 U NA
4 Chloroaniline 7 U NA
4 Chloro 3 methylphenol 16 U NA
4 Nitroaniline 9 U NA
4 Nitrophenol 9 U NA
Acenaphthene 90 J NA
Acenaphthylene 8 U NA
Anthracene 20 J NA
Benzo(a)anthracene 10 J NA
Benzo(b)fluoranthene 11 U NA
Benzo(g,h,i)perylene 7 U NA
Benzo(k)fluoranthene 18 U NA
bis(2 Chloroethyl)ether 6 U NA
bis(2 Ethylhexyl)phthalate 28 U NA
Butyl benzyl phthalate 7 U NA
Chrysene 11 J NA
Dibenzo(a,h)anthracene 9 U NA
Dibenzofuran 53 J NA
Diethyl phthalate 9 U NA
Dimethyl phthalate 7 U NA
Di n octyl phthalate 8 U NA
Fluoranthene 42 J NA
Fluorene 59 J NA
Hexachlorobenzene 8 U NA
Hexachlorobutadiene 12 U NA
Hexachlorocyclopentadiene 64 U NA
Hexachloroethane 10 U NA
Indeno(1,2,3 cd)pyrene 8 U NA
Isophorone 7 U NA
Naphthalene 620 NA
Nitrobenzene 6 U NA
o Cresol(s) (2 Methylphenol) 47 J NA
p Cresol(s) (4 Methylphenol) 29 J NA
Pentachlorophenol 18 U NA
Phenanthrene 110 J NA
Phenol 7 J NA
Pyrene 37 J NA
4,4' DDE 0.22 NA
Aroclor 1221 0.12 U NA
Aroclor 1232 0.095 U NA
Aroclor 1254 0.11 U NA
Aroclor 1260 0.096 U NA
Beta BHC 0.13 NA
Dieldrin 0.0067 U NA
Heptachlor epoxide 0.58 NA
Toxaphene 0.25 U NA
Polychlorinated biphenyls (PCBs) 0.12 U NA
Antimony 5.4 U 5.4 U
Arsenic 35.7 J 30.5 J
Cobalt 7.1 J 6.5 J
Iron 3,600 1,830
Iron and Manganese 3,771 1,982
Lead 227 135
Sodium 187,000 184,000
Thallium 10 U 10 U
Vanadium 19.8 17.1
Zinc 165 62.9
NYSDEC Part 703 Groundwater Quality Objectives
Ground Water
Quality Standards
(ug/L)
VOCs
1,1,2 Trichloroethane 1
1,2 Dichloroethane 0.6
1,2 Dichloroethene (cis) 5*
Acetone 5*
Benzene 1
Bromomethane 5*
Ethylbenzene 5*
Methyl ethyl ketone 5*
Methylene chloride 5*
Toluene 5*
Vinyl Chloride 2
Xylene (mixed) 5*
SVOCs
1,2,4 Trichlorobenzene 5
2 Chlorophenol 5*
2 Methylnaphthalene 5*
2 Nitroaniline 5*
2 Nitrophenol 5*
2,4 Dichlorophenol 5*
2,4 Dimethylphenol 5*
2,4 Dinitrophenol 5*
2,4 Dinitrotoluene 5
2,4,5 Trichlorophenol 5*
2,6 Dinitrotoluene 5
3 Nitroaniline 5*
3,3' Dichlorobenzidine 5
4 Chloroaniline 5
4 Chloro 3 methylphenol 5*
4 Nitroaniline 5*
4 Nitrophenol 5*
Acenaphthene 20
Acenaphthylene 5*
Anthracene 5*
Benzo(a)anthracene 5*
Benzo(b)fluoranthene 5*
Benzo(g,h,i)perylene 5*
Benzo(k)fluoranthene 5*
bis(2 Chloroethyl)ether 5
bis(2 Ethylhexyl)phthalate 5*
Butyl benzyl phthalate 5*
Chrysene 5*
Dibenzo(a,h)anthracene 5*
Dibenzofuran 7 x 10 7
Diethyl phthalate 5*
Dimethyl phthalate 5*
Di n octyl phthalate 5*
Fluoranthene 5*
Fluorene 5*
Hexachlorobenzene 0.04
Hexachlorobutadiene 0.5
Hexachlorocyclopentadiene 5
Hexachloroethane 5
Indeno(1,2,3 cd)pyrene 5*
Isophorone 5*
Naphthalene 5*
Nitrobenzene 0.4
o Cresol(s) (2 Methylphenol) 5*
p Cresol(s) (4 Methylphenol) 5*
Pentachlorophenol 5*
Phenanthrene 5*
Phenol 5*
Pyrene 5*
PCBs/Pesticides
4,4' DDE 0.2
Aroclor 1221 0.09
Aroclor 1232 0.09
Aroclor 1254 0.09
Aroclor 1260 0.09
Beta BHC 0.04
Dieldrin 0.001
Heptachlor epoxide 0.03
Toxaphene 0.06
Polychlorinated biphenyls (PCBs) 0.09
Metals
Antimony 3
Arsenic 25
Cadmium 5*
Cobalt 5*
Iron 300
Iron and Manganese 500
Lead 25
Manganese 300
Selenium 10
Sodium 20,000
Thallium 5*
Vanadium 5*
Zinc 66
* : No criteria established, value is generic criteria
Sample ID:
Laboratory Sample Number:
Sampling Date:
Units: ug/l Q
VOCs
1,2 Dibromo 3 chloropropane < 0.54 U
1,4 Dioxane < 75 U
SVOCs
2,4 Dinitrophenol < 17 U
4 Nitrophenol < 5.4 U
Dibenzofuran < 0.27 U
Hexachlorobenzene < 0.35 U
Hexachlorobutadiene < 0.53 U
Hexachlorocyclopentadiene < 7.4 U
Nitrobenzene < 0.43 U
8/30/2012
JB15285 1
MW 4
Sample ID:
Laboratory Sample Number:
Sampling Date:
Units: ug/l Q
VOCs
1,2 Dibromo 3 chloropropane < 0.54 U
1,4 Dioxane < 75 U
SVOCs
2,4 Dinitrophenol < 17 U
4 Nitrophenol < 5.4 U
Dibenzofuran < 0.28 U
Hexachlorobenzene < 0.35 U
Hexachlorobutadiene < 0.53 U
Hexachlorocyclopentadiene < 7.4 U
Nitrobenzene < 0.44 U
MW 2
JB 15285 3
8/30/2012
Legend
Site Boundary
Existing BuildingBuilding FeaturesFormer AST LocationsFormer AST Pipe Ports
Gowanus Canal
A Monitoring Well Location (ELM, 2004 - 2005)
Water Line
Street Extents
Areas of Concern (AOCs)
Notes:1. Map features are based on aerial photographs, tax maps, and the following ELM reports: Phase II Investigation Report, 363 Bond Street (May 2005) and Phase II Investigation Report, 400 Carroll Street (May 2005).2. All ELM sample locations are approximate and based on the following ELM reports: Phase II Investigation Report, 363 Bond Street (May 2005) and Phase II Investigation Report, 400 Carroll Street (May 2005).3. Italicized values indicate method detection limit exceeds criteria.4. AOC-1: Proposed Excavation Area - 400 Carroll Street, North; AOC-2: Proposed Excavation Area - 400 Carroll Street, South; AOC-3: Proposed Excavation Area - 363 Bond Street; AOC-5: Former UST Area.
BLOCK No. 452, LOT Nos. 1 & 15
Path: \\Langan.com\data\EP\data5\100287501\ArcGIS\ArcMap_Documents\2012-11 - NYSDEC Phase II RIWP\363 Bond Street-400 Carroll Street (Revised 2013-06)\Figure 5 - 363 Bond Data Soil Vapor.mxd
© 2
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LOADING BAYMETAL FLOORELEVATOR
LSV-2
LSV-1
AOC-3
AOC-1
AOC-2
AOC-5
.
50 0 50
SCALE IN FEET
Project Drawing Title
KINGS COUNTY NEW YORK
PSP=_lka=pqobbq
prjj^ov=lc=efpqlof`
plfi=s^mlo=
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Project No.
Date
Scale
Drawn By
Last Revised
Figure
100287501
10/25/2012
amf
6/21/2013
1"=50'
River Drive Center 1, 619 River DriveElmwood Park, NJ 07407-1338
T: 201.794.6900 F: 201.794.0366 www.langan.com
molmlpba=_lka
pqobbq=absbilmjbkq
BROOKLYN
5Langan Engineering & Environmental Services, Inc.
Langan Engineering, Environmental, Surveying andLandscape Architecture, D.P.C.
Langan International LLC
Collectively known as Langan
NJ CERTIFICATE OF AUTHORIZATION No. 24GA27996400
90th Percentile
µg/m3
µg/m3
Volatile Organic Compounds
CIS�1,2�DICHLOROETHYLENE 0.4 <1.9
1,2,4�TRIMETHYLBENZENE 9.8 9.5
1,3�DICHLOROBENZENE 0.5 <2.4
1,3,5�TRIMETHYLBENZENE (MESITYLENE) 3.9 3.7
ACETONE 115 98.9
BENZENE 13 9.4
CARBON DISULFIDE ��� 4.2
CHLOROMETHANE 4.2 3.7
CHLOROFORM 2.81 4.1
CYCLOHEXANE 6.3 ���
DICHLORODIFLUOROMETHANE 10 16.5
ETHYL ACETATE ��� 5.4
ETHYLBENZENE 6.4 5.7
METHYL ETHYL KETONE (2�BUTANONE) 16 12
METHYLENE CHLORIDE 16 to 60 * 10
STYRENE 1.4 1.9
TETRACHLOROETHYLENE(PCE) 2.5 to 100 * 15.9 to 100 *
TOLUENE 57 43
TRICHLOROETHYLENE (TCE) 0.5 to 5 * 4.2
TRICHLOROFLUOROMETHANE 12 18.1
O�XYLENE (1,2�DIMETHYLBENZENE) 7.1 7.9
M AND P XYLENES 11 22.2
CARBON TETRACHLORIDE 1.3 to 5 * 1.3
4�ETHYLTOLUENE ��� 3.6
N�HEPTANE 18 ���
N�HEXANE 14 10.2
USEPA 2001 2
NYSDOH 1
Location ID
Lab Sample Number
Sample Date
Unit
Volatile Organic Compounds
CIS�1,2�DICHLOROETHYLENE 3.8
1,3�DICHLOROBENZENE < 0.9 U
ACETONE 378
CHLOROFORM 214
METHYL ETHYL KETONE (2�BUTANONE) 57.8
TETRACHLOROETHYLENE(PCE) 4160
TRICHLOROETHYLENE (TCE) 379
CARBON TETRACHLORIDE 42
JB15244�2
8/30/2012
ug/m3
LSV�1
Location ID
Lab Sample Number
Sample Date
Unit
Volatile Organic Compounds
CIS�1,2�DICHLOROETHYLENE 88.4
1,3�DICHLOROBENZENE < 0.9 U
CARBON DISULFIDE 4.7
CHLOROFORM 83
TETRACHLOROETHYLENE(PCE) 1010
TRICHLOROETHYLENE (TCE) 2180
CARBON TETRACHLORIDE 87.4
LSV�2
JB15244�3
8/30/2012
ug/m3
Notes:1. Map features are based on aerial photographs, tax maps, and the following ELM reports: Phase II Investigation Report, 363 Bond Street (May 2005) and Phase II Investigation Report, 400 Carroll Street (May 2005).2. All ELM sample locations are approximate and based on the following ELM reports: Phase II Investigation Report, 363 Bond Street (May 2005) and Phase II Investigation Report, 400 Carroll Street (May 2005).3. AOC-1: Proposed Excavation Area - 400 Carroll Street, North; AOC-2: Proposed Excavation Area - 400 Carroll Street, South; AOC-3: Proposed Excavation Area - 363 Bond Street; AOC-5: Former UST Area.
BLOCK No. 452, LOT Nos. 1 & 15
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P-7
P-3
P-2
P-1
P-4
P-9
P-8
P-5
P-6
P-12
P-1BP-1A
P-10
P-11
GP-08
GP-05
GP-10
GP-03GP-04
GP-01GP-11
GP-02 GP-09
GP-06AGP-06B
GP-06C
GP-07C
GP-07A
GP-07B
SB-3
SB-4
SB-11TP
-2
TP
-1
TP-3
TP-5
TP
-4
TP-6
MW-1
SB-6
SB-2
SB-1
SB-7
SB-5
SB-10
SB-12
TP-1
SB-9
MW-43
MW-36
TP-0
TP-8
TP-3
TP-7
TP-6
TP-4TP-2
AOC-1
Path: \\Langan.com\data\EP\data5\100287501\ArcGIS\ArcMap_Documents\2012-11 - NYSDEC Phase II RIWP\363 Bond Street-400 Carroll Street (Revised 2013-07)\Figure 6 - 400 Carroll Data Soil.mxd
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SCALE IN FEET
© 2
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an
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Project No.
Date
Scale
Drawn By
Last Revised
100287501
7/2/2012
amf
7/9/2013
1"=30'
River Drive Center 1, 619 River Drive, Elmwood Park, NJ 07407-1338T: 201.794.6900 F: 201.794.0366 www.langan.com
NEW JERSEY NEW YORK VIRGINIA CALIFORNIA
PENNSYLVANIA CONNECTICUT FLORIDA
Project
KINGS COUNTY NEW YORK
molmlpba=_lka
pqobbq=absbilmjbkqBLOCK No. 452 LOT Nos. 1 & 15
BROOKLYN
Drawing Title
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Figure
6ABU DHABI ATHENS DOHA
DUBAI ISTANBUL
Langan Engineering & Environmental Services, Inc.
Langan Engineering, Environmental, Surveying and Landscape Architecture, D.P.C.
Langan International LLC
Collectively known as Langan
NJ CERTIFICATE OF AUTHORIZATION No. 24GA27996400
Sample ID: TP 1/0.5 3
Laboratory Sample Number:
207935
019
Sampling Date: 10/27/2004
Sampling Depth (ft): 0.5 3
Units: mg/kg Q
Volatile Organic Compounds
1,1 Dichloroethane 0.65 U
1,1 Dichloroethene 0.65 U
1,2 Dichloroethane 0.65 U
1,2 Dichloroethene (cis) 0.65 U
1,2 Dichloroethene (trans) 0.65 U
Acetone 0.82 J
Benzene 0.65 U
Chloroform 0.65 U
Methyl ethyl ketone (MEK / 2
butanone) 0.65 U
Methylene chloride 0.13 JB
Trichloroethene 0.65 U
Vinyl Chloride 0.65 U
Xylene (total) 0.65 U
Semi�Volatile Organic Compounds
o Cresol(s) (2 Methylphenol) 0.42 U
p Cresol(s) (4 Methylphenol) 0.42 U
Pentachlorophenol 2 U
Phenol 0.42 U
Metals
Arsenic 33.3
Copper 85
Lead 232
Mercury (elemental) 0.49
Selenium 6 J
Silver 3.3 U
Zinc 264
Sample ID: TP 1/3 3.5
Laboratory Sample Number:
207935
020
Sampling Date: 10/27/2004
Sampling Depth (ft): 3 3.5
Units: mg/kg Q
Volatile Organic Compounds
1,1 Dichloroethane 0.58 U
1,1 Dichloroethene 0.58 U
1,2 Dichloroethane 0.58 U
1,2 Dichloroethene (cis) 0.58 U
1,2 Dichloroethene (trans) 0.58 U
Acetone 1.5 U
Benzene 0.58 U
Chloroform 0.58 U
Methyl ethyl ketone (MEK / 2
butanone) 0.58 U
Methylene chloride 0.11 JB
Trichloroethene 0.58 U
Vinyl Chloride 0.58 U
Xylene (total) 0.58 U
Semi�Volatile Organic Compounds
Dibenzo (a,h) anthracene 0.37 U
o Cresol(s) (2 Methylphenol) 0.37 U
p Cresol(s) (4 Methylphenol) 0.37 U
Pentachlorophenol 1.8 U
Phenol 0.37 U
Metals
Cadmium 3.7 U
Selenium 19.7 U
Silver 3.7 U
Sample ID: SB 1/4 5
Laboratory Sample Number:
207935
001
Sampling Date: 10/25/2004
Sampling Depth (ft): 4 5
Units: mg/kg Q
Volatile Organic Compounds
1,1 Dichloroethane 0.67 U
1,1 Dichloroethene 0.67 U
1,2 Dichloroethane 0.67 U
1,2 Dichloroethene (cis) 0.67 U
1,2 Dichloroethene (trans) 0.67 U
Acetone 1.7 U
Benzene 0.086 J
Chloroform 0.67 U
Ethylbenzene 8.1
Methyl ethyl ketone (MEK / 2
butanone) 0.67 U
Methylene chloride 0.11 JB
Trichloroethene 0.67 U
Vinyl Chloride 0.67 U
Xylene (total) 0.52 J
Semi�Volatile Organic Compounds
1,2 Dichlorobenzene 1.7 U
Benzo (a) anthracene 1.8
Benzo (a) pyrene 1.7 J
Benzo (b) fluoranthene 1.6 J
Benzo (k) fluoranthene 0.89 J
Chrysene 2
Dibenzo (a,h) anthracene 1.7 U
Indeno (1,2,3 cd) pyrene 0.84 J
o Cresol(s) (2 Methylphenol) 1.7 U
p Cresol(s) (4 Methylphenol) 1.7 U
Pentachlorophenol 8.5 U
Phenol 1.7 U
PCBs/Pesticides
Aroclor 1242 0.15
Metals
Copper 159
Lead 283
Mercury (elemental) 0.84
Nickel 34.5
Selenium 20.8 U
Silver 3.9 U
Zinc 779
Sample ID: SB 3/5 7
Laboratory Sample Number:
207935
003
Sampling Date: 10/25/2004
Sampling Depth (ft): 5 7
Units: mg/kg Q
Volatile Organic Compounds
1,1,1 Trichloroethane 0.69 U
1,1 Dichloroethane 0.69 U
1,1 Dichloroethene 0.69 U
1,2 Dichloroethane 0.69 U
1,2 Dichloroethene (cis) 0.69 U
1,2 Dichloroethene (trans) 0.69 U
Acetone 1.1 J
Benzene 0.13 J
Chloroform 0.69 U
Methyl ethyl ketone (MEK / 2
butanone) 0.69 U
Methylene chloride 0.12 JB
Trichloroethene 0.69 U
Vinyl Chloride 0.69 U
Semi�Volatile Organic Compounds
Dibenzo (a,h) anthracene 0.45 U
o Cresol(s) (2 Methylphenol) 0.45 U
p Cresol(s) (4 Methylphenol) 0.45 U
Pentachlorophenol 2.2 U
Phenol 0.45 U
Metals
Arsenic 43.2
Cadmium 4.2 U
Lead 856
Mercury (elemental) 1.9
Selenium 17.4 J
Silver 5.9
Zinc 1090
Sample ID: SB 5/19 20
Laboratory Sample Number:
207935
005
Sampling Date: 10/25/2004
Sampling Depth (ft): 19 20
Units: mg/kg Q
Semi�Volatile Organic Compounds
Dibenzo (a,h) anthracene 0.4 U
o Cresol(s) (2 Methylphenol) 0.4 U
p Cresol(s) (4 Methylphenol) 0.4 U
Pentachlorophenol 1.9 U
Phenol 0.4 U
Sample ID: TP 3
Laboratory Sample Number: C974508/2
Sampling Date: 10/26/1997
Sampling Depth (ft):
Units: mg/kg Q
Volatile Organic Compounds
Benzene 0.27
Xylene (m,p Xylene) 0.27
Xylene (total) 0.31
Semi�Volatile Organic Compounds
Benzo (a) anthracene 1.1
Benzo (a) pyrene 1.5
Benzo (k) fluoranthene 0.95
Chrysene 1.3
Metals
Mercury (elemental) 2.6
Sample ID:
TP 6/2.7
4.7
Laboratory Sample Number:
207936
004
Sampling Date: 10/27/2004
Sampling Depth (ft): 2.7 4.7
Units: mg/kg Q
Volatile Organic Compounds
1,1 Dichloroethene 0.39 U
1,2 Dichloroethane 0.33 U
1,2 Dichloroethene (cis) 0.38 U
1,2 Dichloroethene (trans) 0.26 U
Acetone 2.4 J
Benzene 0.46 J
Methyl ethyl ketone (MEK / 2
butanone) 0.85 U
Methylene chloride 0.67 JB
Vinyl Chloride 0.29 U
Chrysene 1.0
Xylene (total) 1.1 J
Semi�Volatile Organic Compounds
p Cresol(s) (4 Methylphenol) 0.45 U
Metals
Arsenic 20
Lead 81.8
Mercury (elemental) 2.7
Nickel 75.5
Zinc 997
Sample ID: TP 6
Laboratory Sample Number: C974508/3
Sampling Date: 10/26/1997
Sampling Depth (ft):
Units: mg/kg Q
Volatile Organic Compounds
Benzene 0.2
Xylene (m,p Xylene) 0.35
Xylene (total) 0.41
Metals
Mercury (elemental) 2.6
Sample ID: SB 12/2 4
Laboratory Sample Number:
207936
005
Sampling Date: 10/25/2004
Sampling Depth (ft): 2 4
Units: mg/kg Q
Metals
Lead 129
Sample ID: TP 3/4 7
Laboratory Sample Number:
207936
001
Sampling Date: 10/27/2004
Sampling Depth (ft): 4 7
Units: mg/kg Q
Volatile Organic Compounds
Acetone 0.063
Metals
Copper 79
Lead 305
Mercury (elemental) 0.65
Zinc 131
Sample ID: SB 6/4 6
Laboratory Sample Number:
207935
006
Sampling Date: 10/25/2004
Sampling Depth (ft): 4 6
Units: mg/kg Q
Volatile Organic Compounds
1,1 Dichloroethane 0.62 U
1,1 Dichloroethene 0.62 U
1,2 Dichloroethane 0.62 U
1,2 Dichloroethene (cis) 0.62 U
1,2 Dichloroethene (trans) 0.62 U
Acetone 1.2 J
Benzene 0.62 U
Chloroform 0.62 U
Methyl ethyl ketone (MEK / 2
butanone) 0.62 U
Methylene chloride 0.11 JB
Trichloroethene 0.62 U
Vinyl Chloride 0.62 U
Xylene (total) 0.62 U
Semi�Volatile Organic Compounds
Dibenzo (a,h) anthracene 0.41 U
o Cresol(s) (2 Methylphenol) 0.41 U
p Cresol(s) (4 Methylphenol) 0.41 U
Pentachlorophenol 2 U
Phenol 0.41 U
Metals
Cadmium 4.2 U
Copper 204
Lead 265
Mercury (elemental) 1.2
Selenium 22.4 U
Sample ID: SB 7/14 15
Laboratory Sample Number:
207935
007
Sampling Date: 10/25/2004
Sampling Depth (ft): 14 15
Units: mg/kg Q
Semi�Volatile Organic Compounds
Dibenzo (a,h) anthracene 0.57 U
Indeno (1,2,3 cd) pyrene 0.57 U
o Cresol(s) (2 Methylphenol) 0.57 U
p Cresol(s) (4 Methylphenol) 0.57 U
Pentachlorophenol 2.7 U
Phenol 0.57 U
Sample ID: P 12(4 5)
Laboratory Sample Number: 1204165 5
Sampling Date: 4/12/2012
Sampling Depth (ft): 4 5
Units: mg/kg Q
Volatile Organic Compounds
1,2 Dichloroethane 0.077 U
Acetone 0.45 U
Benzene 0.0942 J
Methyl ethyl ketone (MEK / 2
butanone) 0.296 U
Methylene chloride 0.0601 U
Vinyl Chloride 0.0662 U
Semi�Volatile Organic Compounds
Benzo (a) anthracene 1.83
Benzo (a) pyrene 1.46
Benzo (b) fluoranthene 1.11
Benzo (k) fluoranthene 1.14
Chrysene 1.96
Indeno (1,2,3 cd) pyrene 0.915
Sample ID: P 10(3 4)
Laboratory Sample Number: 1204165 3
Sampling Date: 4/12/2012
Sampling Depth (ft): 3 4
Units: mg/kg Q
Volatile Organic Compounds
1,2 Dichloroethane 0.074 U
Acetone 0.432 U
Benzene 0.112 J
Methyl ethyl ketone (MEK / 2
butanone) 0.284 U
Methylene chloride 0.0577 U
Vinyl Chloride 0.0636 U
1,3 Xylene (m Xylene) 0.273 J
Xylene (m,p Xylene) 0.273 J
Semi�Volatile Organic Compounds
Indeno (1,2,3 cd) pyrene 0.582 J
Sample ID: P 10(7 8)
Laboratory Sample Number: 1204165 4
Sampling Date: 4/12/2012
Sampling Depth (ft): 7 8
Units: mg/kg Q
Volatile Organic Compounds
1,2 Dichloroethane 0.071 U
Acetone 0.415 U
Benzene 0.0611 U
Methyl ethyl ketone (MEK / 2
butanone) 0.273 U
Methylene chloride 0.0554 U
Vinyl Chloride 0.0611 U
SUBPART 375-6 (Revised Brownfields)
UNRESTRICTED
USE
OBJECTIVES
Protection of Public Health
Residential Restricted
Residential
Restricted
Commercial
Restricted
Industrial
(mg/kg) (mg/kg) (mg/kg) (mg/kg) (mg/kg)
VOCs
1,1,1 Trichloroethane 0.68 100 100 500 1,000
1,1 Dichloroethane 0.27 19 26 240 480
1,1 Dichloroethene 0.33 100 100 500 1,000
1,2 Dichloroethane 0.02 2.3 3.1 30 60
1,2 Dichloroethene (cis) 0.25 59 100 500 1,000
1,2 Dichloroethene (trans) 0.19 100 100 500 1,000
Acetone 0.05 100 100 500 1,000
Benzene 0.06 2.9 4.8 44 89
Carbon tetrachloride 0.76 1.4 2.4 22 44
Chlorobenzene 1.1 100 100 500 1,000
Chloroform 0.37 10.00 49 350 700
Ethylbenzene 1 30 41 390 780
Methyl ethyl ketone (MEK / 2 butanone) 0.12 100 100 500 1,000
Methylene chloride 0.05 51 100 500 1,000
Tetrachloroethene 1.3 5.5 19 150 300
Toluene 0.7 100 100 500 1,000
Trichloroethene 0.47 10 21 200 400
Vinyl Chloride 0.02 0.21 0.9 13 27
Propylbenzene n 3.9 100 100 500 1,000
1,2 Xylene (o Xylene) 0.26 100 100 500 1,000
1,3 Xylene (m Xylene) 0.26 100 100 500 1,000
Xylene (m,p Xylene) 0.26 100 100 500 1,000
Xylene (total) 0.26 100 100 500 1,000
SVOCs
1,2 Dichlorobenzene 1.1 100 100 500 1,000
Benzo (a) anthracene 1 1 1 5.6 11
Benzo (a) pyrene 1 1 1 1 1.1
Benzo (b) fluoranthene 1 1 1 5.6 11
Benzo (k) fluoranthene 0.8 1 3.9 56 110
Chrysene 1 1 3.9 56 110
Dibenzo (a,h) anthracene 0.33 0.33 0.33 0.56 1.1
Indeno (1,2,3 cd) pyrene 0.5 0.5 0.5 5.6 11
o Cresol(s) (2 Methylphenol) 0.33 100.00 100 500 1,000
p Cresol(s) (4 Methylphenol) 0.33 34 100 500 1,000
Pentachlorophenol 0.8 2.4 6.7 6.7 55
Phenol 0.33 100 100 500 1,000
PCBs/Pesticides
Aroclor 1242 0.1 1 1 1 25
Metals
Arsenic 13 16 16 16 16
Cadmium 2.5 2.5 4.3 9.3 60
Copper 50 270 270 270 10,000
Lead 63 400 400 1,000 3,900
Mercury (elemental) 0.18 0.81 0.81 2.8 5.7
Nickel 30 140 310 310 10,000
Selenium 3.9 36 180 1,500 6,800
Silver 2 36 180 1,500 6,800
Zinc 109 2200 10000 10000 10000
Sample ID: P 8
Laboratory Sample Number:
1204166
15
Sampling Date: 4/11/2012
Sampling Depth (ft): 4 5
Units: mg/kg Q
Volatile Organic Compounds
1,2 Dichloroethane 0.104 U
1,2 Dichloroethene (cis) 0.374 J
Acetone 0.604 U
Benzene 0.388 J
Methyl ethyl ketone (MEK / 2
butanone) 0.397 U
Methylene chloride 0.0807 U
Vinyl Chloride 0.089 U
1,3 Xylene (m Xylene) 0.328 J
Xylene (m,p Xylene) 0.328 J
Semi�Volatile Organic Compounds
Benzo (a) anthracene 2.56
Benzo (a) pyrene 5.57
Benzo (b) fluoranthene 2.33
Benzo (k) fluoranthene 2.98
Chrysene 2.56
Indeno (1,2,3 cd) pyrene 3.16
Sample ID: P 8
Laboratory Sample Number:
1204166
16
Sampling Date: 4/11/2012
Sampling Depth (ft): 7 7.5
Units: mg/kg Q
Volatile Organic Compounds
Methylene chloride 0.083
Sample ID: P 7
Laboratory Sample Number:
1204166
13
Sampling Date: 4/11/2012
Sampling Depth (ft): 4 5
Units: mg/kg Q
Volatile Organic Compounds
1,2 Dichloroethane 0.172 U
Acetone 1 U
Benzene 0.378 J
Ethylbenzene 1.98
Methyl ethyl ketone (MEK / 2
butanone) 0.659 U
Methylene chloride 0.134 U
Toluene 0.973 J
Vinyl Chloride 0.147 U
1,2 Xylene (o Xylene) 1.11 J
1,3 Xylene (m Xylene) 2.9 J
Xylene (m,p Xylene) 2.9 J
Semi�Volatile Organic Compounds
Benzo (a) anthracene 1.13
Chrysene 1.01
Sample ID: TP 4/4 5
Laboratory Sample Number:
207936
002
Sampling Date: 10/27/2004
Sampling Depth (ft): 4 5
Units: mg/kg Q
Volatile Organic Compounds
1,2 Dichloroethane 0.076 U
Acetone 0.24 U
Benzene 0.065 U
Methyl ethyl ketone (MEK / 2
butanone) 0.2 U
Methylene chloride 0.16 JB
Vinyl Chloride 0.067 U
Metals
Mercury (elemental) 0.18
Sample ID: P 1B
Laboratory Sample Number: 1204166 2
Sampling Date: 4/11/2012
Sampling Depth (ft): 6 7
Units: mg/kg Q
Volatile Organic Compounds
1,2 Dichloroethane 0.076 U
Acetone 0.444 U
Benzene 0.0654 U
Methyl ethyl ketone (MEK / 2
butanone) 0.292 U
Methylene chloride 0.0593 U
Vinyl Chloride 0.0654 U
Sample ID: SB 8/5 7
Laboratory Sample Number:
207935
008
Sampling Date: 10/25/2004
Sampling Depth (ft): 5 7
Units: mg/kg Q
Volatile Organic Compounds
1,1,1 Trichloroethane 3.2 U
1,1 Dichloroethane 3.2 U
1,1 Dichloroethene 3.2 U
1,2 Dichloroethane 3.2 U
1,2 Dichloroethene (cis) 3.2 U
1,2 Dichloroethene (trans) 3.2 U
Acetone 7.9 U
Benzene 0.63 J
Carbon tetrachloride 3.2 U
Chloroform 3.2 U
Chlorobenzene 3.2 U
Ethylbenzene 3.2 U
Methyl ethyl ketone (MEK / 2
butanone) 3.2 U
Methylene chloride 0.56 JB
Tetrachloroethene (start from here) 3.2 U
Toluene 3.2 U
Trichloroethene 3.2 U
Vinyl Chloride 3.2 U
Xylene (total) 3.2 U
Semi�Volatile Organic Compounds
o Cresol(s) (2 Methylphenol) 0.41 U
p Cresol(s) (4 Methylphenol) 0.41 U
Pentachlorophenol 2 U
Phenol 0.41 U
Metals
Cadmium 3.9 U
Mercury (elemental) 0.62
Selenium 20.4 U
Silver 3.8 U
Sample ID: TP 8
Laboratory Sample Number: C974508/5
Sampling Date: 10/26/1997
Sampling Depth (ft):
Units: mg/kg Q
Volatile Organic Compounds
Benzene 1.3
Xylene (m,p Xylene) 0.65
Xylene (total) 0.73
Semi�Volatile Organic Compounds
Benzo (a) anthracene 4.3
Benzo (a) pyrene 3.7
Benzo (b) fluoranthene 3.3
Benzo (k) fluoranthene 3.3
Chrysene 4.2
Dibenzo (a,h) anthracene 0.71
Indeno (1,2,3 cd) pyrene 1.2
Metals
Mercury (elemental) 2.6
Sample ID: P 2
Laboratory Sample Number: 1204166 3
Sampling Date: 4/11/2012
Sampling Depth (ft): 4 5
Units: mg/kg Q
Semi�Volatile Organic Compounds
Benzo (a) anthracene 1.04
Benzo (a) pyrene 1.09
Benzo (k) fluoranthene 0.906
Chrysene 1.06
Indeno (1,2,3 cd) pyrene 0.644
Sample ID: SB 10/1 3
Laboratory Sample Number:
207935
010
Sampling Date: 10/25/2004
Sampling Depth (ft): 1 3
Units: mg/kg Q
Volatile Organic Compounds
1,1 Dichloroethane 0.62 U
1,1 Dichloroethene 0.62 U
1,2 Dichloroethane 0.62 U
1,2 Dichloroethene (cis) 0.62 U
1,2 Dichloroethene (trans) 0.62 U
Acetone 1.5 U
Benzene 0.62 U
Chloroform 0.62 U
Methyl ethyl ketone (MEK / 2
butanone) 0.62 U
Methylene chloride 0.099 JB
Trichloroethene 0.62 U
Vinyl Chloride 0.62 U
Xylene (total) 0.28 J
Semi�Volatile Organic Compounds
1,2 Dichlorobenzene 1.6 U
Benzo (a) anthracene 3.9
Benzo (a) pyrene 4
Benzo (b) fluoranthene 3
Benzo (k) fluoranthene 3.4
Chrysene 4.2
Dibenzo (a,h) anthracene 0.86 J
Indeno (1,2,3 cd) pyrene 2
o Cresol(s) (2 Methylphenol) 1.6 U
p Cresol(s) (4 Methylphenol) 1.6 U
Pentachlorophenol 7.7 U
Phenol 1.6 U
Metals
Cadmium 3.9 U
Copper 131
Lead 222
Mercury (elemental) 0.28
Selenium 20.7 U
Silver 3.9 U
Sample ID: TP 5/1.5 3
Laboratory Sample Number:
207936
003
Sampling Date: 10/27/2004
Sampling Depth (ft): 1.5 3
Units: mg/kg Q
Volatile Organic Compounds
1,1 Dichloroethene 0.35 U
1,2 Dichloroethane 0.3 U
1,2 Dichloroethene (cis) 0.35 U
1,2 Dichloroethene (trans) 0.24 U
Acetone 2.2 J
Benzene 0.78 J
Methyl ethyl ketone (MEK / 2
butanone) 0.77 U
Methylene chloride 0.71 JB
Toluene 0.89 J
Vinyl Chloride 0.27 U
Xylene (total) 2.2 J
Semi�Volatile Organic Compounds
Benzo (a) anthracene 1.5
Benzo (a) pyrene 1.7
Benzo (b) fluoranthene 2.7
Chrysene 1.6
Dibenzo (a,h) anthracene 0.54
Indeno (1,2,3 cd) pyrene 0.92
Metals
Copper 153
Lead 177
Mercury (elemental) 1.6
Zinc 132
Sample ID: GP 10
Laboratory Sample Number:
L1104656
02
Sampling Date: 4/6/2011
Sampling Depth (ft): 25 30
Units: mgkg Q
Volatile Organic Compounds
1,2 Dichloroethane 0.13 U
1,2 Dichloroethene (trans) 0.19 U
Acetone 1.3 U
Benzene 0.13 U
Methyl ethyl ketone (MEK / 2
butanone) 1.3 U
Methylene chloride 1.3 U
Vinyl Chloride 0.25 U
Sample ID: P 3
Laboratory Sample Number: 1204166 5
Sampling Date: 4/11/2012
Sampling Depth (ft): 3.5 5
Units: mg/kg Q
Volatile Organic Compounds
1,2 Dichloroethane 0.248 U
Acetone 1.45 U
Benzene 0.214 U
Methyl ethyl ketone (MEK / 2
butanone) 0.954 U
Methylene chloride 0.194 U
Vinyl Chloride 0.214 U
1,3 Xylene (m Xylene) 0.427 U
Xylene (m,p Xylene) 0.427 U
Semi�Volatile Organic Compounds
Benzo (a) anthracene 11.3 E
Benzo (a) pyrene 14.6 E
Benzo (b) fluoranthene 10.4
Benzo (k) fluoranthene 11.9 E
Chrysene 10.5
Dibenzo (a,h) anthracene 3.87
Sample ID: SB 9/3 5
Laboratory Sample Number:
207935
009
Sampling Date: 10/25/2004
Sampling Depth (ft): 3 5
Units: mg/kg Q
Volatile Organic Compounds
1,2 Dichloroethane 0.031 U
Acetone 0.14
Vinyl Chloride 0.031 U
Xylene (total) 0.28
Semi�Volatile Organic Compounds
1,2 Dichlorobenzene 3.2 U
Benzo (a) anthracene 7.5
Benzo (a) pyrene 6.7
Benzo (b) fluoranthene 5.5
Benzo (k) fluoranthene 5.3
Chrysene 7.5
Dibenzo (a,h) anthracene 1.7 J
Indeno (1,2,3 cd) pyrene 3.8
o Cresol(s) (2 Methylphenol) 3.2 U
p Cresol(s) (4 Methylphenol) 3.2 U
Pentachlorophenol 16 U
Phenol 3.2 U
Sample ID: P 4
Laboratory Sample Number: 1204166 7
Sampling Date: 4/11/2012
Sampling Depth (ft): 3.5 5
Units: mg/kg Q
Volatile Organic Compounds
1,2 Dichloroethane 0.158 U
Acetone 0.92 U
Benzene 0.135 U
Methyl ethyl ketone (MEK / 2
butanone) 0.605 U
Methylene chloride 0.123 U
Vinyl Chloride 0.135 U
1,3 Xylene (m Xylene) 0.271 U
Xylene (m,p Xylene) 0.271 U
Semi�Volatile Organic Compounds
Benzo (a) anthracene 1.36
Benzo (a) pyrene 1.15
Benzo (b) fluoranthene 1.01
Benzo (k) fluoranthene 1.04
Chrysene 1.4
Indeno (1,2,3 cd) pyrene 0.78
Sample ID: P 4
Laboratory Sample Number: 1204166 8
Sampling Date: 4/11/2012
Sampling Depth (ft): 6 7
Units: mg/kg Q
Volatile Organic Compounds
Methylene chloride 0.0545
Sample ID: TP 7
Laboratory Sample Number: C974508/4
Sampling Date: 10/26/1997
Sampling Depth (ft):
Units: mg/kg Q
Volatile Organic Compounds
Benzene 0.15
Xylene (m,p Xylene) 0.29
Xylene (total) 0.35
Sample ID: GP 04
Laboratory Sample Number:
L1104348
04
Sampling Date: 3/30/2011
Sampling Depth (ft): 25 30
Units: mgkg Q
Semi�Volatile Organic Compounds
Pentachlorophenol 0.88 U
Sample ID: P 6
Laboratory Sample Number:
1204166
11
Sampling Date: 4/11/2012
Sampling Depth (ft): 4 5
Units: mg/kg Q
Volatile Organic Compounds
1,2 Dichloroethane 0.0805 U
Acetone 0.47 U
Benzene 0.0692 U
Methyl ethyl ketone (MEK / 2
butanone) 0.309 U
Methylene chloride 0.0628 U
Vinyl Chloride 0.0692 U
Sample ID: SB 2/9 10
Laboratory Sample Number:
207935
002
Sampling Date: 10/25/2004
Sampling Depth (ft): 9 10
Units: mg/kg Q
Semi�Volatile Organic Compounds
Dibenzo (a,h) anthracene 0.57 U
Indeno (1,2,3 cd) pyrene 0.57 U
o Cresol(s) (2 Methylphenol) 0.57 U
p Cresol(s) (4 Methylphenol) 0.57 U
Pentachlorophenol 2.8 U
Phenol 0.57 U
Sample ID: SB 4/3 5
Laboratory Sample Number:
207935
004
Sampling Date: 10/25/2004
Sampling Depth (ft): 3 5
Units: mg/kg Q
Volatile Organic Compounds
1,1 Dichloroethene 0.62 U
1,2 Dichloroethane 0.62 U
1,2 Dichloroethene (cis) 0.62 U
1,2 Dichloroethene (trans) 0.62 U
Acetone 3.6
Benzene 0.11 J
Chloroform 0.62 U
Methyl ethyl ketone (MEK / 2
butanone) 0.62 U
Methylene chloride 0.11 JB
Trichloroethene 0.62 U
Vinyl Chloride 0.62 U
Xylene (total) 0.41 J
Semi�Volatile Organic Compounds
o Cresol(s) (2 Methylphenol) 0.4 U
p Cresol(s) (4 Methylphenol) 0.4 U
Pentachlorophenol 1.9 U
Phenol 0.4 U
Metals
Cadmium 3.7 U
Lead 93.9
Selenium 20 U
Silver 3.7 U
Sample ID: P 5
Laboratory Sample Number: 1204166 9
Sampling Date: 4/11/2012
Sampling Depth (ft): 3.5 5
Units: mg/kg Q
Volatile Organic Compounds
Acetone 0.42
Methylene chloride 0.132
Sample ID: P 5
Laboratory Sample Number:
1204166
10
Sampling Date: 4/11/2012
Sampling Depth (ft): 7 7.5
Units: mg/kg Q
Volatile Organic Compounds
1,2 Dichloroethane 0.224 U
Acetone 1.31 U
Benzene 0.192 U
Methyl ethyl ketone (MEK / 2
butanone) 0.858 U
Methylene chloride 0.174 U
Vinyl Chloride 0.192 U
1,3 Xylene (m Xylene) 0.384 U
Xylene (m,p Xylene) 0.384 U
Sample ID: SB 11/4 5
Laboratory Sample Number:
207935
012
Sampling Date: 10/25/2004
Sampling Depth (ft): 4 5
Units: mg/kg Q
Volatile Organic Compounds
1,1,1 Trichloroethane 3.4 U
1,1 Dichloroethane 3.4 U
1,1 Dichloroethene 3.4 U
1,2 Dichloroethane 3.4 U
1,2 Dichloroethene (cis) 3.4 U
1,2 Dichloroethene (trans) 3.4 U
Acetone 8.5 U
Benzene 3.4 U
Carbon tetrachloride 3.4 U
Chlorobenzene 3.4 U
Chloroform 3.4 U
Ethylbenzene 3.4 U
Methyl ethyl ketone (MEK / 2
butanone) 3.4 U
Methylene chloride 0.56 JB
Tetrachloroethene (start from here) 3.4 U
Toluene 3.4 U
Trichloroethene 3.4 U
Vinyl Chloride 3.4 U
Xylene (total) 3.4 U
Semi�Volatile Organic Compounds
1,2 Dichlorobenzene 1.8 U
Benzo (a) anthracene 4.1
Benzo (a) pyrene 11
Benzo (b) fluoranthene 4.5
Benzo (k) fluoranthene 5.7
Chrysene 4.2
Dibenzo (a,h) anthracene 1.8
Indeno (1,2,3 cd) pyrene 7.2
o Cresol(s) (2 Methylphenol) 1.8 U
p Cresol(s) (4 Methylphenol) 1.8 U
Pentachlorophenol 8.8 U
Phenol 1.8 U
Metals
Cadmium 4.4 U
Copper 76
Lead 139
Selenium 23.4 U
Silver 4.4 U
Zinc 211
Sample ID:
SB 11/14
15
Laboratory Sample Number:
207935
011
Sampling Date: 10/25/2004
Sampling Depth (ft): 14 15
Units: mg/kg Q
Semi�Volatile Organic Compounds
Dibenzo (a,h) anthracene 0.59 U
Indeno (1,2,3 cd) pyrene 0.59 U
o Cresol(s) (2 Methylphenol) 0.59 U
p Cresol(s) (4 Methylphenol) 0.59 U
Pentachlorophenol 2.8 U
Phenol 0.59 U
Sample ID: P 9(3.5 5)
Laboratory Sample Number: 1204165 1
Sampling Date: 4/12/2012
Sampling Depth (ft): 3.5 5
Units: mg/kg Q
Volatile Organic Compounds
1,2 Dichloroethane 0.236 U
Acetone 1.38 U
Benzene 0.203 U
Methyl ethyl ketone (MEK / 2
butanone) 0.906 U
Methylene chloride 0.184 U
Propylbenzene n 9.2
Vinyl Chloride 0.203 U
1,3 Xylene (m Xylene) 0.771 J
Xylene (m,p Xylene) 0.771 J
Semi�Volatile Organic Compounds
Benzo (a) anthracene 3.03
Benzo (a) pyrene 5.84
Benzo (b) fluoranthene 2.76
Benzo (k) fluoranthene 3.52
Chrysene 3.24
Dibenzo (a,h) anthracene 0.67
Indeno (1,2,3 cd) pyrene 3.57
Areas of Concern (AOCs)
Legend
Site Boundary
Former Building
Former AST Locations
Former AST Pipe Ports
Gowanus Canal
Sample Locations
A Monitoring Well/Piezometer Location (ELM, 2004 - 2005)
Test Pit Location (Zeb Environmental, 2012)"/
Test Pit Location (Cosmo Environmental, 1997)S
Water Line
Street Extents
!. Soil Boring Location (ELM, 2004 - 2005)
D!. Soil Boring & Temporary Well Location (ELM, 2004 - 2005)
Test Pit Location (ELM, 2004 - 2005)
!. Geoprobe Location (PW Grosser, 2011)
A Monitoring Well Location (PW Grosser, 2011)
Test Pit Location (PW Grosser, 2011)
Notes:1. Map features are based on aerial photographs, tax maps, and the following ELM reports: Phase II Investigation Report, 363 Bond Street (May 2005), and Phase II Investigation Report, 400 Carroll Street (May 2005).2. All ELM sample locations are approximate and based on the following ELM reports: Phase II Investigation Report, 363 Bond Street (May 2005), and Phase II Investigation Report, 400 Carroll Street (May 2005).3. Italicized values indicate method detection limit exceeds criteria.4. AOC-1: Proposed Excavation Area - 400 Carroll Street, North; AOC-2: Proposed Excavation Area - 400 Carroll Street, South; AOC-3: Proposed Excavation Area - 363 Bond Street; AOC-5: Former UST Area
D!.
D!.
D!.
D!.
D!.
D!.
A
A
A
GO
WA
NU
S C
AN
AL
BO
ND
ST
RE
ET
LOADING BAY
METAL FLOOR
SB-3
SB-11
MW-1
SB-6
SB-2
SB-7
SB-12
MW-43
MW-36
MW-2
AOC-3
AOC-1
AOC-2
AOC-5
Path: \\Langan.com\data\EP\data5\100287501\ArcGIS\ArcMap_Documents\2012-11 - NYSDEC Phase II RIWP\363 Bond Street-400 Carroll Street (Revised 2013-07)\Figure 7 - 400 Carroll Data Groundwater.mxd
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SCALE IN FEET
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Project No.
Date
Scale
Drawn By
Last Revised
100287501
7/2/2012
amf
7/9/2013
1"=30'
River Drive Center 1, 619 River Drive, Elmwood Park, NJ 07407-1338T: 201.794.6900 F: 201.794.0366 www.langan.com
NEW JERSEY NEW YORK VIRGINIA CALIFORNIA
PENNSYLVANIA CONNECTICUT FLORIDA
Project
KINGS COUNTY NEW YORK
molmlpba=_lka
pqobbq=absbilmjbkqBLOCK No. 452, LOT Nos. 1 & 15
BROOKLYN
Drawing Title
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Figure
7ABU DHABI ATHENS DOHA
DUBAI ISTANBUL
Langan Engineering & Environmental Services, Inc.
Langan Engineering, Environmental, Surveying and Landscape Architecture, D.P.C.
Langan International LLC
Collectively known as Langan
NJ CERTIFICATE OF AUTHORIZATION No. 24GA27996400
Notes:1. Map features are based on aerial photographs, tax maps, and the following ELM reports: Phase II Investigation Report, 363 Bond Street (May 2005), and Phase II Investigation Report, 400 Carroll Street (May 2005).2. All ELM sample locations are approximate and based on the following ELM reports: Phase II Investigation Report, 363 Bond Street (May 2005), and Phase II Investigation Report, 400 Carroll Street (May 2005).3. Italicized values indicate method detection limit exceeds criteria.4. AOC-1: Proposed Excavation Area - 400 Carroll Street, North; AOC-2: Proposed Excavation Area - 400 Carroll Street, South; AOC-3: Proposed Excavation Area - 363 Bond Street; AOC-5: Former UST Area
Sample ID: SB�3/W
Laboratory Sample Number:
207935�
014
Sampling Date: 10/27/2004
Units: ug/l Q
Volatile Organic Compounds
1,1,1�Trichloroethane 5 U
1,1�Dichloroethane 5 U
1,1�Dichloroethene 5 U
1,1,1�Trichloroethane 5 U
1,1,2�Trichloroethane 5 U
1,1,2,2�Tetrachloroethane 5 U
1,2�Dichloroethane 5 U
1,2�Dichloroethene (cis) 5 U
1,2�Dichloroethene (trans) 5 U
Acetone 13
Benzene 1.7 J
Bromomethane 5 U
Carbon Disulfide 5 U
Chlorobenzene 5 U
Chloroethane 5 U
Ethylbenzene 5 U
Methyl ethyl ketone 10 U
Methylene chloride 5 UB
4�Methyl�2�Pentanone 10 U
Styrene 5 U
Tetrachloroethene 5 U
Toluene 5 U
Trichloroethene 5 U
Vinyl Chloride 5 U
Xylene (mixed) 5 U
Semi�Volatile Organic Compounds
1,2,4�Trichlorobenzene 10 U
2�Chlorophenol 10 U
2�Methylnaphthalene 10 U
2�Nitroaniline 50 U
2�Nitrophenol 10 U
2,4�Dichlorophenol 10 U
2,4�Dimethylphenol 10 U
2,4�Dinitrophenol 50 U
2,4�Dinitrotoluene 10 U
2,4,5�Trichlorophenol 50 U
2,6�Dinitrotoluene 10 U
3�Nitroaniline 50 U
3,3'�Dichlorobenzidine 20 U
4�Chloroaniline 10 U
4�Chloro�3�methylphenol 10 U
4�Nitroaniline 20 U
4�Nitrophenol 50 U
Acenaphthylene 10 U
Anthracene 10 U
Benzo(a)anthracene 10 U
Benzo(b)fluoranthene 10 U
Benzo(g,h,i)perylene 10 U
Benzo(k)fluoranthene 10 U
bis(2�Chloroethyl)ether 10 U
bis(2�Ethylhexyl)phthalate 10 U
Butyl benzyl phthalate 10 U
Chrysene 10 U
Dibenzo(a,h)anthracene 10 U
Dibenzofuran 0.8 J
Diethyl phthalate 10 U
Dimethyl phthalate 10 U
Di�n�octyl phthalate 10 U
Fluoranthene 10 U
Hexachlorobenzene 10 U
Hexachlorobutadiene 10 U
Hexachlorocyclopentadiene 10 U
Hexachloroethane 10 U
Indeno(1,2,3�cd)pyrene 10 U
Isophorone 10 U
Naphthalene 10 U
Nitrobenzene 10 U
o�Cresol(s) (2�Methylphenol) 10 U
p�Cresol(s) (4�Methylphenol) 10 U
Pentachlorophenol 50 U
Phenanthrene 10 U
Phenol 10 U
Pyrene 10 U
PCBs/Pesticides
Aroclor 1016 0.5 U
Aroclor 1221 1 U
Aroclor 1232 0.5 U
Aroclor 1242 0.5 U
Aroclor 1248 0.5 U
Aroclor 1254 0.5 U
Aroclor 1260 1 U
Metals
Antimony 20 U
Arsenic 40 U
Cadmium 10 U
Cobalt 10 U
Iron 426
Manganese 440
Selenium 30 U
Sodium 20,100
Thallium 40 U
Vanadium 6 U
Sample ID: SB�12/TW
Laboratory Sample Number:
207935�
018
Sampling Date: 10/27/2004
Units: ug/l Q
Volatile Organic Compounds
1,1,1�Trichloroethane 5 U
1,1�Dichloroethane 5 U
1,1�Dichloroethene 5 U
1,1,1�Trichloroethane 5 U
1,1,2�Trichloroethane 5 U
1,1,2,2�Tetrachloroethane 5 U
1,2�Dichloroethane 5 U
1,2�Dichloroethene (cis) 5 U
1,2�Dichloroethene (trans) 5 U
Bromomethane 5 U
Carbon Disulfide 5 U
Carbon tetrachloride 5 U
Chlorobenzene 5 U
Chloroethane 5 U
Ethylbenzene 5 U
Methyl ethyl ketone 10 U
Methylene chloride 5 UB
4�Methyl�2�Pentanone 10 U
Styrene 5 U
Tetrachloroethene 5 U
Toluene 5 U
Trichloroethene 5 U
Vinyl Chloride 5 U
Xylene (mixed) 5 U
Semi�Volatile Organic Compounds
1,2,4�Trichlorobenzene 10 U
2�Chlorophenol 10 U
2�Methylnaphthalene 10 U
2�Nitroaniline 50 U
2�Nitrophenol 10 U
2,4�Dichlorophenol 10 U
2,4�Dimethylphenol 10 U
2,4�Dinitrophenol 50 U
2,4�Dinitrotoluene 10 U
2,4,5�Trichlorophenol 50 U
2,6�Dinitrotoluene 10 U
3�Nitroaniline 50 U
3,3'�Dichlorobenzidine 20 U
4�Chloroaniline 10 U
4�Chloro�3�methylphenol 10 U
4�Nitroaniline 20 U
4�Nitrophenol 50 U
Acenaphthylene 10 U
Anthracene 10 U
Benzo(a)anthracene 10 U
Benzo(b)fluoranthene 10 U
Benzo(g,h,i)perylene 10 U
Benzo(k)fluoranthene 10 U
bis(2�Chloroethyl)ether 10 U
bis(2�Ethylhexyl)phthalate 10 U
Butyl benzyl phthalate 10 U
Chrysene 10 U
Dibenzo(a,h)anthracene 10 U
Dibenzofuran 10 U
Diethyl phthalate 10 U
Dimethyl phthalate 10 U
Acenaphthylene 10 U
Anthracene 10 U
Benzo(a)anthracene 10 U
Benzo(b)fluoranthene 10 U
Benzo(g,h,i)perylene 10 U
Benzo(k)fluoranthene 10 U
bis(2�Chloroethyl)ether 10 U
bis(2�Ethylhexyl)phthalate 10 U
Butyl benzyl phthalate 10 U
Chrysene 10 U
Dibenzo(a,h)anthracene 10 U
Dibenzofuran 10 U
Diethyl phthalate 10 U
Dimethyl phthalate 10 U
Di�n�octyl phthalate 10 U
Fluoranthene 10 U
Fluorene 10 U
Hexachlorobenzene 10 U
Hexachlorobutadiene 10 U
Hexachlorocyclopentadiene 10 U
Hexachloroethane 10 U
Indeno(1,2,3�cd)pyrene 10 U
Isophorone 10 U
Naphthalene 10 U
Nitrobenzene 10 U
o�Cresol(s) (2�Methylphenol) 10 U
p�Cresol(s) (4�Methylphenol) 10 U
Pentachlorophenol 50 U
Phenol 10 U
Pyrene 10 U
PCBs/Pesticides
Aroclor 1016 0.5 U
Aroclor 1221 1 U
Aroclor 1232 0.5 U
Aroclor 1242 0.5 U
Aroclor 1248 0.5 U
Aroclor 1254 0.5 U
Aroclor 1260 1 U
Metals
Antimony 20 U
Arsenic 40 U
Cadmium 10 U
Cobalt 10 U
Iron 1540
Manganese 344
Selenium 30 U
Sodium 93,400
Thallium 40 U
Sample ID: SB�6/TW
Laboratory Sample Number:
207935�
015
Sampling Date: 10/27/2004
Units: ug/l Q
Volatile Organic Compounds
1,1,1�Trichloroethane 5 U
1,1�Dichloroethane 5 U
1,1�Dichloroethene 5 U
1,1,1�Trichloroethane 5 U
1,1,2�Trichloroethane 5 U
1,1,2,2�Tetrachloroethane 5 U
1,2�Dichloroethane 5 U
1,2�Dichloroethene (cis) 5 U
1,2�Dichloroethene (trans) 5 U
Acetone 8.4 J
Benzene 1 J
Bromomethane 5 U
Carbon Disulfide 5 U
Carbon tetrachloride 5 U
Chlorobenzene 5 U
Chloroethane 5 U
Ethylbenzene 5 U
Methyl ethyl ketone 10 U
Methylene chloride 5 UB
4�Methyl�2�Pentanone 10 U
Styrene 5 U
Tetrachloroethene 5 U
Toluene 5 U
Trichloroethene 5 U
Vinyl Chloride 5 U
Xylene (mixed) 5 U
Semi�Volatile Organic Compounds
1,2,4�Trichlorobenzene 10 U
2�Chlorophenol 10 U
2�Methylnaphthalene 10 U
2�Nitroaniline 50 U
2�Nitrophenol 10 U
2,4�Dichlorophenol 10 U
2,4�Dimethylphenol 10 U
2,4�Dinitrophenol 50 U
2,4�Dinitrotoluene 10 U
2,4,5�Trichlorophenol 50 U
2,6�Dinitrotoluene 10 U
3�Nitroaniline 50 U
3,3'�Dichlorobenzidine 20 U
4�Chloroaniline 10 U
4�Chloro�3�methylphenol 10 U
4�Nitroaniline 20 U
4�Nitrophenol 50 U
Acenaphthylene 10 U
Anthracene 10 U
Benzo(a)anthracene 10 U
Benzo(b)fluoranthene 10 U
Benzo(g,h,i)perylene 10 U
Benzo(k)fluoranthene 10 U
bis(2�Chloroethyl)ether 10 U
bis(2�Ethylhexyl)phthalate 10 U
Butyl benzyl phthalate 10 U
Chrysene 10 U
Dibenzo(a,h)anthracene 10 U
Dibenzofuran 10 U
Diethyl phthalate 10 U
Dimethyl phthalate 10 U
Di�n�octyl phthalate 10 U
Hexachlorobenzene 10 U
Hexachlorobutadiene 10 U
Hexachlorocyclopentadiene 10 U
Hexachloroethane 10 U
Indeno(1,2,3�cd)pyrene 10 U
Isophorone 10 U
Naphthalene 10 U
Nitrobenzene 10 U
o�Cresol(s) (2�Methylphenol) 10 U
p�Cresol(s) (4�Methylphenol) 10 U
Pentachlorophenol 50 U
Phenol 10 U
PCBs/Pesticides
Aroclor 1016 0.52 U
Aroclor 1221 1 U
Aroclor 1232 0.52 U
Aroclor 1242 0.52 U
Aroclor 1248 0.52 U
Aroclor 1254 0.52 U
Aroclor 1260 1 U
Metals
Antimony 8.3 J
Cadmium 10 U
Cobalt 10 U
Iron 4,900
Manganese 621
Selenium 30 U
Sodium 913,000
Thallium 40 U
Vanadium 6 U
Sample ID: SB�7/TW
Laboratory Sample Number:
207935�
016
Sampling Date: 10/27/2004
Units: ug/l Q
Volatile Organic Compounds
1,1,1�Trichloroethane 5 U
1,1�Dichloroethane 5 U
1,1�Dichloroethene 5 U
1,1,1�Trichloroethane 5 U
1,1,2�Trichloroethane 5 U
1,1,2,2�Tetrachloroethane 5 U
1,2�Dichloroethane 5 U
1,2�Dichloroethene (cis) 5 U
1,2�Dichloroethene (trans) 5 U
Acetone 7.4 J
Benzene 5 U
Bromomethane 5 U
Carbon Disulfide 5 U
Carbon tetrachloride 5 U
Chlorobenzene 5 U
Chloroethane 5 U
Ethylbenzene 5 U
Methyl ethyl ketone 10 U
Methylene chloride 5 UB
4�Methyl�2�Pentanone 10 U
Styrene 5 U
Tetrachloroethene 5 U
Toluene 5 U
Trichloroethene 5 U
Vinyl Chloride 5 U
Benzene 1 J
Semi�Volatile Organic Compounds
1,2,4�Trichlorobenzene 10 U
2�Chlorophenol 10 U
2�Methylnaphthalene 10 U
2�Nitroaniline 50 U
2�Nitrophenol 10 U
2,4�Dichlorophenol 10 U
2,4�Dimethylphenol 10 U
2,4�Dinitrophenol 50 U
2,4�Dinitrotoluene 10 U
2,4,5�Trichlorophenol 50 U
2,6�Dinitrotoluene 10 U
3�Nitroaniline 50 U
3,3'�Dichlorobenzidine 20 U
4�Chloroaniline 10 U
4�Chloro�3�methylphenol 10 U
4�Nitroaniline 20 U
4�Nitrophenol 50 U
Acenaphthylene 10 U
Benzo(b)fluoranthene 10 U
Benzo(g,h,i)perylene 10 U
Benzo(k)fluoranthene 10 U
bis(2�Chloroethyl)ether 10 U
bis(2�Ethylhexyl)phthalate 10 U
Butyl benzyl phthalate 10 U
Chrysene 10 U
Dibenzo(a,h)anthracene 10 U
Dibenzofuran 10 U
Diethyl phthalate 10 U
Dimethyl phthalate 10 U
Di�n�octyl phthalate 10 U
Hexachlorobenzene 10 U
Hexachlorobutadiene 10 U
Hexachlorocyclopentadiene 10 U
Hexachloroethane 10 U
Indeno(1,2,3�cd)pyrene 10 U
Isophorone 10 U
Naphthalene 10 U
Nitrobenzene 10 U
o�Cresol(s) (2�Methylphenol) 10 U
p�Cresol(s) (4�Methylphenol) 10 U
Pentachlorophenol 50 U
Phenol 10 U
PCBs/Pesticides
Aroclor 1016 0.58 U
Aroclor 1221 1.2 U
Aroclor 1232 0.58 U
Aroclor 1242 0.58 U
Aroclor 1248 0.58 U
Aroclor 1254 0.58 U
Aroclor 1260 0.11 J
Metals
Antimony 20 U
Arsenic 40 U
Cadmium 10 U
Cobalt 10 U
Iron 3,540
Manganese 315
Selenium 30 U
Sodium 83,300
Thallium 40 U
Vanadium 6 U
Sample ID: SB�2/TW
Laboratory Sample Number:
207935�
013
Sampling Date: 10/27/2004
Units: ug/l Q
Volatile Organic Compounds
1,1,1�Trichloroethane 5 U
1,1�Dichloroethane 5 U
1,1�Dichloroethene 5 U
1,1,1�Trichloroethane 5 U
1,1,2�Trichloroethane 5 U
1,1,2,2�Tetrachloroethane 5 U
1,2�Dichloroethane 5 U
1,2�Dichloroethene (cis) 5 U
1,2�Dichloroethene (trans) 5 U
Acetone 6.6 J
Benzene 8.8
Bromomethane 5 U
Carbon Disulfide 5 U
Carbon tetrachloride 5 U
Chlorobenzene 5 U
Chloroethane 5 U
Ethylbenzene 5 U
Methyl ethyl ketone 10 U
Methylene chloride 5 UB
4�Methyl�2�Pentanone 10 U
Styrene 5 U
Tetrachloroethene 5 U
Trichloroethene 5 U
Vinyl Chloride 5 U
Semi�Volatile Organic Compounds
1,2,4�Trichlorobenzene 10 U
2�Chlorophenol 10 U
2�Methylnaphthalene 10 U
2�Nitroaniline 50 U
2�Nitrophenol 10 U
2,4�Dichlorophenol 10 U
2,4�Dimethylphenol 10 U
2,4�Dinitrophenol 50 U
2,4�Dinitrotoluene 10 U
2,4,5�Trichlorophenol 50 U
2,6�Dinitrotoluene 10 U
3�Nitroaniline 50 U
3,3'�Dichlorobenzidine 20 U
4�Chloroaniline 10 U
4�Chloro�3�methylphenol 10 U
4�Nitroaniline 20 U
4�Nitrophenol 50 U
Acenaphthylene 10 U
Anthracene 10 U
Benzo(a)anthracene 10 U
Benzo(b)fluoranthene 10 U
Benzo(g,h,i)perylene 10 U
Benzo(k)fluoranthene 10 U
bis(2�Chloroethyl)ether 10 U
bis(2�Ethylhexyl)phthalate 10 U
Butyl benzyl phthalate 10 U
Chrysene 10 U
Dibenzo(a,h)anthracene 10 U
Dibenzofuran 10 U
Diethyl phthalate 10 U
Dimethyl phthalate 10 U
Di�n�octyl phthalate 10 U
Fluoranthene 10 U
Fluorene 10 U
Hexachlorobenzene 10 U
Hexachlorobutadiene 10 U
Hexachlorocyclopentadiene 10 U
Hexachloroethane 10 U
Indeno(1,2,3�cd)pyrene 10 U
Isophorone 10 U
Naphthalene 10 U
Nitrobenzene 10 U
o�Cresol(s) (2�Methylphenol) 10 U
p�Cresol(s) (4�Methylphenol) 10 U
Pentachlorophenol 50 U
Phenanthrene 10 U
Phenol 10 U
Pyrene 10 U
PCBs/Pesticides
Aroclor 1016 0.54 U
Aroclor 1221 1.1 U
Aroclor 1232 0.54 U
Aroclor 1242 0.54 U
Aroclor 1248 0.54 U
Aroclor 1254 0.54 U
Aroclor 1260 1.1 U
Metals
Antimony 20 U
Arsenic 40 U
Cadmium 10 U
Cobalt 10 U
Selenium 30 U
Sodium 83,000
Thallium 40 U
Sample ID: SB�11/TW
Laboratory Sample Number:
207935�
017
Sampling Date: 10/27/2004
Units: ug/l Q
Volatile Organic Compounds
1,1,1�Trichloroethane 5 U
1,1�Dichloroethane 5 U
1,1�Dichloroethene 5 U
1,1,1�Trichloroethane 5 U
1,1,2�Trichloroethane 5 U
1,1,2,2�Tetrachloroethane 5 U
1,2�Dichloroethane 5 U
1,2�Dichloroethene (cis) 5 U
1,2�Dichloroethene (trans) 5 U
Acetone 9.6 J
Benzene 33
Bromomethane 5 U
Carbon tetrachloride 5 U
Chlorobenzene 5 U
Chloroethane 5 U
Methyl ethyl ketone 10 U
Methylene chloride 5 UB
4�Methyl�2�Pentanone 10 U
Styrene 5 U
Tetrachloroethene 5 U
Toluene 5.5
Trichloroethene 5 U
Vinyl Chloride 5 U
Xylene (mixed) 17
Semi�Volatile Organic Compounds
1,2,4�Trichlorobenzene 20 U
2�Chlorophenol 20 U
2�Nitroaniline 100 U
2�Nitrophenol 20 U
2,4�Dichlorophenol 20 U
2,4�Dimethylphenol 20 U
2,4�Dinitrophenol 100 U
2,4�Dinitrotoluene 20 U
2,4,5�Trichlorophenol 100 U
2,6�Dinitrotoluene 20 U
3�Nitroaniline 100 U
3,3'�Dichlorobenzidine 40 U
4�Chloroaniline 20 U
4�Chloro�3�methylphenol 20 U
4�Nitroaniline 40 U
4�Nitrophenol 100 U
Acenaphthene 89
Acenaphthylene 20 U
Anthracene 5 J
Benzo(b)fluoranthene 20 U
Benzo(k)fluoranthene 20 U
bis(2�Chloroethyl)ether 20 U
bis(2�Ethylhexyl)phthalate 20 U
Butyl benzyl phthalate 20 U
Dibenzo(a,h)anthracene 20 U
Dibenzofuran 20 U
Diethyl phthalate 20 U
Dimethyl phthalate 20 U
Di�n�octyl phthalate 20 U
Fluoranthene 7 J
Fluorene 31
Hexachlorobenzene 20 U
Hexachlorobutadiene 20 U
Hexachlorocyclopentadiene 20 U
Hexachloroethane 20 U
Indeno(1,2,3�cd)pyrene 20 U
Naphthalene 10 J
Nitrobenzene 20 U
o�Cresol(s) (2�Methylphenol) 20 U
p�Cresol(s) (4�Methylphenol) 20 U
Pentachlorophenol 100 U
Phenanthrene 47
Phenol 20 U
Pyrene 10 J
PCBs/Pesticides
Aroclor 1016 0.5 U
Aroclor 1221 1 U
Aroclor 1232 0.5 U
Aroclor 1242 0.5 U
Aroclor 1248 0.5 U
Aroclor 1254 0.5 U
Aroclor 1260 1 U
Metals
Antimony 20 U
Arsenic 40 U
Cadmium 10 U
Cobalt 10 U
Iron 751
Selenium 30 U
Sodium 57,600
Thallium 40 U
NYSDEC Part 703 Groundwater Quality Objectives
Ground Water Quality
Standards
Part 703***
(ug/L)
VOCs
1,1,1�Trichloroethane 5*
1,1�Dichloroethane 5*
1,1�Dichloroethene 5*
1,1,1�Trichloroethane 5*
1,1,2�Trichloroethane 1
1,1,2,2�Tetrachloroethane 5*
1,2�Dichloroethane 0.6
1,2�Dichloroethene (cis) 5*
1,2�Dichloroethene (trans) 5*
1,2,4�Trimethylbenzene 5*
Acetone 5*
Benzene 1
Bromomethane 5*
Carbon Disulfide 5*
Carbon tetrachloride 5*
Chlorobenzene 5*
Chloroethane 5*
Ethylbenzene 5*
Isopropyl Benzene 5*
Methyl ethyl ketone (MEK / 2�butanone) 5*
Methylene chloride 5*
4�Methyl�2�Pentanone 5*
Sec�Butylbenzene 5*
Styrene 5*
Tert�Butylbezene 5*
Tetrachloroethene 5*
Toluene 5*
Trichloroethene 5*
Vinyl Chloride 2
1,2�Xylene (o�Xylene) 5*
Xylene (mixed) 5*
SVOCs
1,2,4�Trichlorobenzene 5*
2�Chlorophenol 5*
2�Methylnaphthalene 5*
2�Nitroaniline 5*
2�Nitrophenol 5*
2,4�Dichlorophenol 5*
2,4�Dimethylphenol 5*
2,4�Dinitrophenol 5*
2,4�Dinitrotoluene 5*
2,4,5�Trichlorophenol 5*
2,6�Dinitrotoluene 5*
3�Nitroaniline 5*
3,3'�Dichlorobenzidine 5*
4�Chloroaniline 5*
4�Chloro�3�methylphenol 5*
4�Nitroaniline 5*
4�Nitrophenol 5*
Acenaphthene 20
Acenaphthylene 5*
Anthracene 5*
Benzo(a)anthracene 5*
Benzo(b)fluoranthene 5*
Benzo(g,h,i)perylene 5*
Benzo(k)fluoranthene 5*
bis(2�Chloroethyl)ether 5*
bis(2�Ethylhexyl)phthalate 5*
Butyl benzyl phthalate 5*
Chrysene 5*
Dibenzo(a,h)anthracene 5*
Dibenzofuran 7 x 10�7
Diethyl phthalate 5*
Dimethyl phthalate 5*
Di�n�octyl phthalate 5*
Fluoranthene 5*
Fluorene 5*
Hexachlorobenzene 0.04
Hexachlorobutadiene 0.5
Hexachlorocyclopentadiene 5*
Hexachloroethane 5*
Indeno(1,2,3�cd)pyrene 5*
Isophorone 5*
Naphthalene 5*
Nitrobenzene 0.4
o�Cresol(s) (2�Methylphenol) 5*
p�Cresol(s) (4�Methylphenol) 5*
Pentachlorophenol 5*
Phenanthrene 5*
Phenol 5*
Pyrene 5*
PCBs
Aroclor 1016 0.09
Aroclor 1221 0.09
Aroclor 1232 0.09
Aroclor 1242 0.09
Aroclor 1248 0.09
Aroclor 1254 0.09
Aroclor 1260 0.09
Metals
Antimony 3
Arsenic 25
Cadmium 5*
Cobalt 5*
Iron 300
Manganese 300
Selenium 10
Sodium 20,000
Thallium 5*
Vanadium 5*
* : No criteria established, value is generic criteria
Areas of Concern (AOCs)
Legend
Site Boundary
Former Building
Former AST Locations
Former AST Pipe Ports
Gowanus Canal
A Monitoring Well Location (ELM, 2004 - 2005)
Water Line
Street Extents
D!. Soil Boring & Temporary Well Location (ELM, 2004 - 2005)
Monitoring Well Location (PW Grosser, 2011)A
Path: \\Langan.com\data\EP\data5\100287501\ArcGIS\ArcMap_Documents\2012-11 (Rev. 2013-07) - NYSDEC Phase II RIWP\363 Bond Street-400 Carroll Street (Revised 2013-07)\Figure 8 - Summary of NAPL Observations.mxd
© 2
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AOC-3
AOC-1
AOC-2
AOC-5
SHELVES
RACKS
LSB-4LSB-3
MW-2
SB-4LSB-2
SB-5
LSV-1
LSV-2
LSB-1
P-7
P-3
P-2
P-1
P-4
P-9
P-8
P-5
P-6
P-12
P-1BP-1A
P-10
P-11
GP-08
GP-05
GP-10
GP-03GP-04
GP-01GP-11
GP-02 GP-09
GP-06AGP-06B
GP-06C
GP-07C
GP-07AGP-07B
MW-43
MW-36
SB-9
SB-7
SB-4
SB-2
SB-5SB-1
SB-6SB-3
SB-10
SB-11
SB-12
MW-1
SB-8
MW-3
MW-5
MW-4
MW-1
SB-1
SB-3
SB-2
TP-1TP-0
TP-8
TP-3
TP-7
TP-6
TP-4TP-2
.
40 0 40
SCALE IN FEET
Project Drawing Title
KINGS COUNTY NEW JERSEY
prjj^ov=lc
k^mi=l_pbos^qflkp
Project No.
Date
Scale
Drawn By
Last Revised
Figure
100287501
11/6/2012
amf
7/10/2013
1"=40'
River Drive Center 1, 619 River DriveElmwood Park, NJ 07407-1338
T: 201.794.6900 F: 201.794.0366 www.langan.com
molmlpba=_lka=
pqobbq=absbilmjbkqBLOCK No. 452, LOT Nos. 1 & 15
BROOKLYN
8Langan Engineering & Environmental Services, Inc.
Langan Engineering, Environmental, Surveying andLandscape Architecture, D.P.C.
Langan International LLC
Collectively known as Langan
NJ CERTIFICATE OF AUTHORIZATION No. 24GA27996400
Legend
Sheen Observed
DNAPL Observed
LNAPL Observed
Historic Sample Location!R
Areas of Concern (AOCs)
Proposed Excavation Area (Langan)
Street Extents
Gowanus Canal
Water Line
Former AST Pipe Ports
Former AST Locations
Building Features
Existing Building
Former Building
Site Boundary
Notes:1. Map features are based on aerial photographs, tax maps, and the following ELM reports: Phase II Investigation Report, 363 Bond Street (May 2005); and Phase II Investigation Report, 400 Carroll Street (May 2005).2. AOC-1: Proposed Excavation Area - 400 Carroll Street, North; AOC-2: Proposed Excavation Area - 400 Carroll Street, South; AOC-3: Proposed Excavation Area - 363 Bond Street; AOC-5: Former UST Area
Path: \\Langan.com\data\EP\data5\100287501\ArcGIS\ArcMap_Documents\2012-11 (Rev. 2013-07) - NYSDEC Phase II RIWP\363 Bond Street-400 Carroll Street (Revised 2013-07)\Figure 9 - Proposed Phase II Sample Location Plan.mxd
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NU
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AL
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ST
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1ST STREET
LOADING BAY
METAL FLOOR
ELEVATOR
AOC-3
AOC-1
AOC-2
AOC-5
LSV-2
LSV-1
LSB-4LSB-3
LSB-2LSB-1
LSV-15
LSV-14
LSV-11
LSV-13
LSV-12
LSV-5
LSV-4
LSV-3LSV-16
LSV-17
LSV-18 LSV-19 LSV-20
LSV-1
LSV-2
LSB-9
LSB-5
LSB-7
LSB-8
LSB-6
LSB-23 LSB-24
LSB-21/LMW-10
LSB-10
LSB-22/LMW-6
LSB-25/LMW-7
LSB-27/LMW-9
.
40 0 40
SCALE IN FEET
Project Drawing Title
KINGS COUNTY NEW YORK
molmlpba
p^jmib=il`^qflk=
mi^k
Project No.
Date
Scale
Drawn By
Last Revised
Figure
100287501
11/6/2012
amf
7/10/2013
1"=40'
River Drive Center 1, 619 River DriveElmwood Park, NJ 07407-1338
T: 201.794.6900 F: 201.794.0366 www.langan.com
molmlpba=_lka
pqobbq=absbilmjbkqBLOCK No. 452, LOT Nos. 1 & 15
BROOKLYN
9Langan Engineering & Environmental Services, Inc.
Langan Engineering, Environmental, Surveying andLandscape Architecture, D.P.C.
Langan International LLC
Collectively known as Langan
NJ CERTIFICATE OF AUTHORIZATION No. 24GA27996400
Legend
Site Boundary
Former Building
Former AST Locations
Water Line
Gowanus Canal
Streets
Area of Concern
Former AST Pipe Ports
Proposed Excavation Extents (Langan)
Historic Test Pit Location
Historic Monitoring Well/Piezometer LocationA
Historic Test Pit Location"
Historic Soil Boring/Geoprobe Location!
Due Diligence Soil Vapor Point Location A
Due Diligence Soil Boring Location A
Due Diligence Soil Boring/Monitoring Well Location A
Proposed Soil Vapor Point Location A
Proposed Soil Boring Location A
Proposed Soil Boring/Monitoring Well Location A
Historic Soil Boring/Temporary Well Location!D
Notes:1. Map features are based on aerial photographs, tax maps, and the following ELM reports: Phase II Investigation Report, 363 Bond Street (May 2005), and Phase II Investigation Report, 400 Carroll Street (May 2005).2. All ELM sample locations are approximate and based on the following ELM reports: Phase II Investigation Report, 363 Bond Street (May 2005), and Phase II Investigation Report, 400 Carroll Street (May 2005).3. AOC-1: Proposed Excavation Area - 400 Carroll Street, North; AOC-2: Proposed Excavation Area - 400 Carroll Street, South; AOC-3: Proposed Excavation Area - 363 Bond Street; AOC-5: Former UST Area
Remedial Investigation Work Plan Proposed 363 Bond Street Development
APPENDIX A
ARCHITECTURAL DRAWINGS
,J
-
EL. 9' -8"
-N N
EL. 8'-6"
EL. 10' -8"
1
CARROLL STREET (601
) (NIIRROW STREE11 , , ~n
NYC OWNED P
MECHANICAL
COMMUNITY FACILITY
RESIDENTIAL
__j <( u
~ :r: u w :::;>
RESIDENTIAL
GROUND FLOOR 1" = 30'-o"
RESIDENTIAL
PARKING
RES LOBBY
RES LOBBY
PARKING
2ND STREET (601)
(NARROW STREET]
EL. 6' -4"
RECREATION SPACE
RECREATION SPACE
CARROLL STREET BRIDGE
_j <( u z: <( :r: u w :::;>
__j <(
fz: w 0 (/) w IY
RESIDENTIAL
22' EL. 3'-6"
G) 0
~ z c (f)
§; z )> r
NOTE: FOR ILLUSTRATIVE PURPOSES ONLY
NOTE: SHORELINE CONDITION AND BULKHEAD LOCATION MAY VARY AS REQUIREED BY N y s DEPARTMENT OF ENVIROMENTAL CONSERVATION AND THE us ARMY CORPS OF ENGIN.EERS
363-365 Bond Street
Client:
Goldstein, Hill & West Architects, LLP 11 Broadway, Suite 1700 New York, NY 10004 Tel212.213.8007 Fax 212.686.1754
The Lightstone Group 460 Park Avenue, Suite 1300 New York, NY 10022 Tel: 212.616.9969
Landscape Architects:
Lee Weintraub Landscape Architects 59 Edgecliff Ter Yonkers, NY 10705 Tel: 917.965-6540
Project:
363-365 Bond Street Brooklyn, NY
8/21/2012 MODIFICATION SUBMISSION
6/19/2012 CPC DRAFT
No. Date Revision
ULURP SUBMISSION Title:
Ground Floor
Seal & Signature Date: Project No.: 11 F79 SCALE:
Z-6 cadd file no.: P:\11 F79
Remedial Investigation Work Plan Proposed 363 Bond Street Development
APPENDIX B
PREVIOUS ENVIRONMENTAL REPORTS
Remedial Investigation Work Plan Proposed 363 Bond Street Development
APPENDIX C
PREVIOUS CORRESPONDENCE
1
Karen Nespolini
From: David Yudelson <[email protected]>Sent: Tuesday, November 06, 2012 12:17 PMTo: Christopher McMahon; Steve CiambruschiniSubject: FW: 400 Carroll StreetAttachments: 400 Carroll Street Comments 01 11 12.pdf
From: Brian Carr [mailto:[email protected]]Sent: Friday, May 04, 2012 3:27 PMTo: David YudelsonCc: Christos TsiamisSubject: 400 Carroll Street
David,
Called but you were not available. I spent a number of hours going over the draft Order with mymanagement. Their primary focus is reaching a determination on the scope of the covenant for this, and whetherHQ-approval is required. I don't see any other drafting issues that can't be resolved. I will be in touch ASAP.
On the technical side, EPA has reviewed the conceptual wall design and the only issue identified, the possibilitythat there is unknown contamination at other locations laterally along the bulkhead, is addressed by the fact thatthe cut-off wall is expected to go along the entire frontage of the parcel. Our consultants comments are attachedFYI. Accordingly, the conceptual approach is approved. When your consultant has prepared a detailed design,EPA would like to review that.
We are happy to discuss this further if you have questions.
Thanks for your patience and cooperation,
Brian E. CarrAssistant Regional CounselUnited States Environmental Protection AgencyRegion 2Office of Regional Counsel290 Broadway, 17th FloorNew York, NY 10007(212) 637-3170 phone(212) 637-3104 [email protected]
1
M E M O R A N D U M
400 Carroll Street Document Review USEPA
PREPARED BY: CH2M HILL
DATE: January 11, 2012
PROJECT NUMBER: 422395.DE.02
At the request of the USEPA Region 2, CH2M HILL reviewed two documents related to proposed remedial activities being conducted at 400 Carroll Street in Brooklyn, New York (Site). The Site is located within Remedial Target Area (RTA 1) of the Gowanus Canal Superfund Site, as defined in the recent draft Feasibility Study (December, 2011) prepared by CH2M HILL for USEPA Region 2. A subsurface investigation was conducted in 2011 at the Site to delineate the extent of soil impacts in the vicinity of monitoring well GC‐MW43 (Grosser, 2011a). The well was installed as part of the Gowanus Canal Remedial Investigation performed in 2010 (HDR, 2011). The layout of the Site is shown in Figure 1. The 2011 investigation found that non‐aqueous phase liquid (NAPL) identified as coal tar/creosote was present in the subsurface at the Site at depths ranging from approximately 30 to 35 feet below ground surface (bgs). Additional evidence of NAPL staining and sheens was observed at depths ranging from 4 ft bgs to 30 ft bgs. Based upon the type of NAPL identified in the Site subsurface and the concentrations in Site soil compared to Canal sediments, the subsurface investigation report concluded that the NAPL was likely entering the subsurface below the Site from the Canal. A cross section was created across GC‐MW43 (installed as part of the 2010 RI) and boring GP05 (installed as part of the 2011 investigation of the Site), both located on the Site, and boring GC‐SD19C located in the Canal (also installed as part of the 2010 RI), to examine the relationship between NAPL impacts in Site soils and in Canal sediments. The location of the cross section is shown in Figure 2, while the cross section is presented in Figure 3. The boring logs for GC‐MW43, GP‐05, and GC‐SD19C used to construct the cross section are included as Attachment A. In boring GP‐05, only the interval from 25‐30 ft bgs was logged. The fine silty sand observed in this interval had observable free product NAPL present. In GC‐MW43, evidence of NAPL staining or sheen was observed from 4 to 7 ft bgs and again from 25 to 30 ft bgs. Free product was observed in a layer of clayey sand from 30 to 32.5 ft bgs, and another thin lens of free product was observed at 34.5 ft bgs, atop another layer of clayey sand. The sediment boring in the Canal (GC‐SD19C) covered the distance from the top of the soft organic sediment layer (mud line), located at an elevation of ‐8 ft NAVD 88 (corresponding to approximately 18 feet bgs on the upland Site). The boring captured 6.5 feet of soft sediment, and extended an additional 5 ft into the underlying native sediment to a total depth of ‐19.5 ft NAVD 88 (11.5 ft below the mud line, corresponding to an upland Site location of approximately ‐29.5 ft bgs). NAPL staining and coating was observed in the native sediment portion of the core. No NAPL effects were observed in the soft sediment portion of the core. As shown by the cross‐section, NAPL effects are more widespread vertically throughout the Site soils than in the Canal sediments. Additionally, no free product was observed in the Canal sediments in front of the site, while free product was observed in the Site soils. The groundwater in GC‐MW43 was measured at an elevation of approximately 3 feet below ground surface (bgs) (corresponding to an elevation of 7 ft NAVD88) in July 2010. The mean lower level water (MLLW) elevation of the canal is 0 ft NAVD88, or approximately 10 feet below the Site ground surface. The resulting groundwater gradient indicates that shallow groundwater at the Site would flow toward the canal, as was found to be the case for other upland sites along the canal (HDR, 2011). Groundwater discharging into the Canal from the Site indicates that
PREPARED FOR:
400 CARROLL STREET DOCUMENT REVIEW
2
contaminants would likely not be transported based on hydrodynamic forces from the Canal to the Site, as they would have to move against the groundwater gradient. A NAPL gradient from the canal to the upland soils would be needed to transport NAPL upland. This situation does not appear to currently exist, but could have in the history of the canal use. There is an Outfall pipe located along the cross section in question that was speculated to be involved in contaminant transport between the Canal and Upland sites. However, examination of the Outfall survey records from the Remedial Investigation showed that the outfall is located at the tidal interface, between 3 and 0 ft NAVD88. Because this outfall is above the Canal water surface except at high tide, and located well above the elevations where NAPL was observed in the Canal sediments, it is unlikely that the Outfall and associated sewer piping serves as a NAPL transport pathway from the Canal to the Site. Based on the initial conclusions of the Site Investigation, a remedial alternative was proposed that consisted of installing a watertight barrier extending from 20‐35 ft bgs (‐10 to ‐25 ft NAVD88) between the Site and the existing bulkhead along the Canal (Grosser, 2011b). The type of sheet piling proposed in Grosser (2011b) was not specified. CH2M HILL agrees that an impervious barrier with sealed joints and constructed of appropriate materials would likely provide a sufficient barrier for the mitigation of NAPL transport between the Site and the Canal. More clarification is needed to ascertain whether the proposed barrier wall is of sufficient length and depth. While placement of the proposed barrier wall appears to extend above and below the measured NAPL impacts, the data available at GP‐05 may not have completely captured the top and bottom of the NAPL contamination, as the boring was only logged between 25 and 30 ft bgs and product was observed within the complete 25‐30 ft bgs interval (see Figure 3). The memorandum (Grosser, 2011b) does not specify the proposed length of barrier wall to be installed along the Canal. Additional NAPL characterization along the proposed barrier wall is recommended to determine the vertical and lateral extent of NAPL contamination before a final bulkhead barrier wall depth and length are finalized. The barrier depth 10 feet into the native sediment layer (35 ft bgs) appears to be sufficient if significant NAPL impacts are not present below GP‐05. References: HDR, CH2M HILL, and GRB Environmental Services, Inc. (2011). Gowanus Canal Remedial Investigation Report
Volume 1. Prepared for United States Environmental Protection Agency (USEPA). January. P.W. Grosser Consulting. (2011a). DRAFT Subsurface Investigation Summary Report 400 Carroll Street –Brooklyn,
New York. September 13. P.W. Grosser Consulting. (2011b). Bulkhead Replacement – 400 Carroll Street, Brooklyn, NY. October 25.
Native SedimentsGlacial Deposits (silts, sands and gravels)
Soft Sediment
10 ft
0 ft
-10 ft
-20 ft
-30 ft
-40 ft
-50 ft
-60 ft
-70 ft
Elev
atio
n (fe
et N
AVD
88 A
ppro
xim
ate)
-8 ft
-14.5 ft
FIGURE 3400 Carroll Street Cross SectionBrooklyn, New York
GP-05GCMW-43S
GC-SD19C
Bulkhead
NAPL Sheen, Coating, Staining, or Blebs
NAPL Saturation
Legend
Outfall GC-CF-W-043
Well Screen
Sand
SandClayey Sand
Clayey Sand
Clayey Sand
Silty Sand
Silty Clay
Fill – Sand and Gravel
Water Level
Possible Location of Sewer Line
Sand with Silt and GravelProposed Barrier Wall
Project No: SERAS-059
Project: Gowanus Canal Superfund Site
Client: EP AlERT
Location: 400 Carroll St., Brooklyn, NY
Logged By: J. Bolduc
..c -0. <I> 0
SUBSURFACE PROFILE
0 ..0 E >. (/)
Description
Gravel With Sand (GW-SW) Fill Very dark gray, fine and coarse gravel, some fine and coarse sand, little sill, trace well rounded cobbles, coal, brick, and occasional wood fragments, loose, wet, petroleum hydrocarbon sheen and moderate to strong petroleum hydrocarbon odor at 4 feet, strong petroleum hydrocarbon odor at 7 feet.
Silty Clay (CL) Dark gray, low plasticity, soft, plant remains to 15 feet, occasional shell fragments throughout, wet.
GCMW-43S Northing (ft): 186235.390 Log of Well: GCMW-4 GCMW-43S Easting (ft): 987143.769
GCMW-431 Northing (ft): 186235.575
GCMW-431 Easting (ft): 987143.829
GCMW-43S Elevation (ft AMSL): 5.39
GCMW-431 Elevation (ft AMSL): 5.40
SAMPLE
'-<!> .0 E ::I z
<I> 0.
~
2:' <I> > 0 u <I> 0 cr::
0.0
PID Readings ppmv
20 40 60 80 100
12.2 . 3.4
2.8
0.0
0.0
0.0
0.0
0.0
0.0 • 0.0
Well Completion Details
E=:~~...,..,.----------+-~~.r~~-t-+--1 o.o Clayey Sand (SC) Grayish brown, fine grained, some clay, wet.
Drill Method: A300 Rotary Sonic
Start Date: 1300 5/17/10
Hole Size: 8 inches
0.0 • 0.0 •
0.0 • 0.0 .
Lockheed Martin/SERAS 2890 Woodbridge Avenue Building 209 Annex Edison, NJ 08837
Drill Company: Boart Longyear
End Date: 1843 5/17/10
Sheet: 1 of 2
Project No: SERAS-059
Project: Gowanus Canal Superfund Site
Client: EPNERT
Location: 400 Carroll St. , Brooklyn, NY
Logged By: J. Bolduc
.£:
a. (!)
0
SUBSURFACE PROFILE
0 .0 E >. (j)
Description
Silty Sand (SM) Grayish brown, fine grained, trace medium to coarse grained, some silt, wet, spotty petroleum hydrocarbon sheens, faint petroleum hydrocarbon odor. Three.fnch thick wet lens& of silty fine sub rounded gravel and fine sand at 28 feet.
Clayey Sand (SC) Grayish brown, fine grained, some clay, micaceous, dark gray petroleum hydrocarbon staining throughout, stained intervals are saturated with low viscosity brown petroleum
Sand(SP) Very dark g rayish brown, fine grained, trace silt, wet, saturated wi th low viscosity petroleum hydrocarbon In 3· inch thick interval at bottom, strong
odor.
Drill Method: A300 Rotary Sonic
Start Date: 1300 5/17/10
Hole Size: 8 inches
GCMW-43S Northing (ft): 186235.390 Log of Well: GCMW-4 GCMW-43S Easting (ft): 987143.769
GCMW-431 Northing (ft): 186235.575
GCMW-431 Easting (ft): 987143.829
GCMW-43S Elevation (ft AMSL): 5.39
GCMW-431 Elevation (ft AMSL): 5.40
SAMPLE
Well Completion Details '-(!) PID Readings
ppmv ~ :> (!)
.0 E ::J z
0
_,,0
20 40 60 80 100 iJJ
0.0 ~--~~~~--~ ·
13.0
13.0
0.0
0.0 . 0.0 • 0.0
~-=c~=-f.~l----1---1 'o.o
•
15.0
15.0 •
15.0
50.0 •
Lockheed Martin/SERAS 2890 Woodbridge Avenue Building 209 Annex Edison, NJ 08837
Drill Company: Boart Longyear
End Date: 1843 5/17/1 0
Sheet: 2 of 2
Logged By:
0 5 0.0 NA
5 5
10 5
15 5
20 5
25 5 5.0 SP
30 5
Hand Cleared
2.5"
DNEZY
WBL1001400 Carrol Street
GP-05East Stepout Project Manager:
Project Number:
P.W. GROSSER CONSULTING
Depth(ft)
Advance(ft)
Recovery(ft)
GraphicLog
Boring Designation:Boring Location:Project Name:
PAL Environmental
Soil Description
Macro Core
14:55
Direct PushDrilling Method:
Borehole Depth: 30'
Sampling Method:
Completion Time:13:30
Drilling Contractor:Driller Name:
Start Time:
Mike Baldwin
Start Date:
Borehole Diameter:
USCS Code Notes
3/30/2011 3/30/2011Completion Date:
PID - 67.9 ppmFine sand, silt, very dark gray (10YR3/1), wet. (Freeproduct observed)
Pre-probed to 25'
E.O.B. @ 30'
Page 5 of 9
Attempt 1 Refusal? Y/N
Attempt 2 Refusal? Y/N
Site Name: Gowanus Canal Sediment Coring InvestigationProject Number: 395863
Project Location: Gowanus Canal, Brooklyn, New York
Sampling M. Velasquez/CH2M HILL Northing: 672227.64 Penetration (ft): 16' Y
Survey Duration: March-April 2010
Station ID: GC-SD19C Easting: 633769.29
J. Balas/CH2M HILL Datum: NYSP Zone East NAD 83 Date/Time: 3/11/2010 13:50
Crew/Company R. Clennon/CH2M HILL Elevation: -6.4' NAVD88 Recovery (ft) 11.5'
Vessel: R/V Manasquan St.Depart: 14:35 Penetration (ft): NA
ASI - M. Shappell/Captain Depth (ft): 5.7'
St. Arrival: 13:45
Collector Information: T. Himmer/CH2M HILL Log reflects sample as collected – no correction factor
applied for less than 100% core recovery
Date/Time:
Collection: vibracore Logged by: Michael Murphy Recovery (ft)
Depth
below
mud
line (
ft)
Litho
logy
Type
Color (
Munse
ll)
Consis
tency
/ Den
sity
Cemen
tation
/ Plas
ticity
Structu
re
Moistur
e Con
tent
Maxim
um pa
rticle
size
Odor
% grav
el
% san
d
% fine
s
PID R
eadin
g (pp
m)
Sample
IDs (
Single
Lette
r)
Commen
ts
NA
OL 10YR VS N H Wet CS UNC 0% 3% 97%2/1
1 33.1
2
3 11.3
4
5 23.2
Organic: fibrous wood, leaves, and stick fragments
NA
NA
NA
6
6.56.8
7 SW-SM 10YR H N H Wet FS PHC 0% 75% 25% 25.14/3 (strong)
32.88
33.4
9 ML 10YR F N H Wet VFS PHC 0% 90% 10%4/4 (mod) 29.9
SW-SM 10YR H N H Wet FS PHC 15% 60% 25%10 4/4 (strong) 39.1
soil dilatency
No staining or discoloration on soil pores*
Well graded sand with silt and gravel
Transition zone - not sampled
*Well graded sand with siltNAPL coating - blebs of NAPL rising via gravity/
* Single small cobble (subrounded)NAPL staining on and around cobble - slick, lowviscosity, not sticky, brown staining
Additional Notes/Comments: Bottom of core at 11.5'. Core opened at 08:30. * Indicates VOC collection depth.
NA
A
B
141 of 280
Depth
below
mud
line (
ft)
Litho
logy
Type
Color (
Munse
ll)
Consis
tency
/ Den
sity
Cemen
tation
/ Plas
ticity
Structu
re
Moistur
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tent
Maxim
um pa
rticle
size
Odor
% grav
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% san
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% fine
s
PID R
eadin
g (pp
m)
Sample
IDs (
Single
Lette
r)
Commen
ts
SW-SM 10YR H N H Wet FS PHC 15% 60% 25%4/3 (strong) 34.5
11BOC= 94.111.5
12
13
14
15
16
17
18
19
Single small cobble (subrounded)
*
B
C
20Sample Summary:
TCL
VOC
s
TCL
SVO
Cs
TCL
Pest
icid
es
TCL
PCB
s
TAL
Met
als
+ H
g
Cya
nide
TOC
Sulfi
de
Gra
in S
ize
Arc
hive
TCLP
RIC
A X X X X X X X X X X
B X X X X X X X X X X
C X X X X X X X X X X
DEFGHIJKLMNOPQRSTU
Reviewed by: Date:
Sample ID
Sample Type
(N/FD/MSD) Sample Date/TimeDepth Interval
(ft)
GC-SD019C-06.8-08.8 N 03/12/2010 08:30 6.8-8.8GC-SD019C-08.8-10.8 N 03/12/2010 08:30 8.8-10.8GC-SD019C-10.8-11.5 N 03/12/2010 08:30 10.8-11.5
TMHimmer 3/12/2010
142 of 280
DEPARTMENT OF CITY PLANNING CITY OF NEW YORK
ENVIRONMENTAL ASSESSMENT AND REVIEW DIVISION
Amanda M. Burden, FAICP, Director Department of City Planning
Robert Dobruskin, AICP. Director James P. Merani, Deputy Director
22 Reade Street, New York, N.Y. 10007-1216 Room 4E (212) 720-3420 FAX (212) 720-3495
February 6, 2009 NOTICE OF COMPLETION OF
THE FINAL ENVIRONMENTAL IMPACT STATEMENT
363-365 Bond Street Project Identification Lead Agency CEQR# 08DCP033K City Planning Commission ULURP#s C090047 ZMK, C090048 ZSK, N090049 ZRK 22 Reade Street, 1W SEQRA Classification: Type I New York, NY 10007 Contact Person Robert Dobruskin, AICP, Director (212) 720-3423 Environmental Assessment and Review Division New York City Department of City Planning Pursuant to City Environmental Quality Review (CEQR), Mayoral Executive Order No. 91 of 1977, CEQR Rules of Procedure of 1991 and the regulations of Article 8 of the State Environmental Conservation Law, State Environmental Quality Review Act (SEQRA) as found in 6 NYCRR Part 617, a Final Environmental Impact Statement (FEIS) has been prepared for the action described below. Copies of the FEIS are available for public inspection at the office of the undersigned. The proposal involves actions by the City Planning Commission and Council of the City of New York pursuant to Uniform Land Use Review Procedures (ULURP). A public hearing on the Draft Environmental Impact Statement (DEIS) was held on Wednesday, January 7th, 2009. Comments were requested on the DEIS and were received and considered by the Lead Agency until Tuesday, January 20th, 2009. This FEIS incorporates responses to the public comments received on the DEIS and additional analysis conducted subsequent to the completion of the DEIS. The proposed action is classified as a SEQRA Type I action.
A. PROJECT IDENTIFICATION
Toll Brothers, Inc., (“the applicant”), is seeking discretionary City and State actions in connection with the redevelopment of two blocks located along the west waterfront of the Gowanus Canal in the Gowanus neighborhood of Brooklyn Community District 6. The proposed actions would facilitate a proposal by the applicant to redevelop the parcels with a mix of residential (market rate and affordable), commercial, community facility, and open space uses.
The proposed actions include a zoning text amendment (to Zoning Resolution (ZR) sections 123-63 and 123-90) and a related zoning map amendment to change an existing M2-1 zoning district to a Special Mixed Use District: M1-4/R7-2 (MX). The rezoning would affect two blocks along the west waterfront of the Gowanus Canal. The area of the proposed rezoning is bounded
Final EIS Notice of Completion 363-365 Bond Street, CEQR No.08DCP033K by the midpoints of Carroll Street to the north, Bond Street to the west, 2nd Street to the south, and the channel of the Gowanus Canal to the east. If the proposed rezoning is approved it would allow redevelopment of the project site which encompasses Brooklyn Tax Block 452 (Lots 1 and 15) and Tax Block 458 (Lot 1). Two City-owned parcels on Block 452 (lots 5 and 19), one of which is occupied by an Emergency Medical Services (EMS) facility and the other of which is infrastructure associated with the historic Carroll Street Bridge, are not part of the project site (the area the applicant seeks to redevelop), but are included in the area to be rezoned. Although the text amendment would apply to the entire rezoning area, no new development is expected to occur on these City-owned properties as a result of the proposed actions.
In addition, as part of the proposed actions, sections 23-144, 23-922 and 23-942 would be amended to apply the Inclusionary Housing Program and related floor area regulations to R7-2 zoning districts within the proposed special mixed use district, and to provide for a base FAR of 2.7 and a maximum FAR of 3.6 within the special district. These amendments would add R7-2 districts within Community District 6 in Brooklyn to the list of residential districts in which the Inclusionary Housing Program would be applicable within certain designated areas, and would add the proposed Special Mixed-Use District (specified geographically), as one of the Inclusionary Housing designated districts.
Finally, the applicant is seeking a special permit pursuant to ZR section 74-743 to modify the following requirements within a General Large-Scale Development: (i) height and setback regulations for all buildings in special mixed use districts pursuant to ZR section 123-662; (ii) inner courtyard recess regulations pursuant to ZR section 23-852; and (iii) required rear yards in residential and mixed use districts pursuant to ZR sections 23-45 and 123-651.
Discretionary approvals from State and federal agencies, including the New York State Department of Environmental Conservation (DEC), and U.S. Army Corps of Engineers (ACOE) will also be required, since the project proposes new stormwater outfalls to the Gowanus Canal, the installation of a new sheet-pile bulkhead along the canal, and possible dewatering during construction.
The applicant shall record a Restrictive Declaration that will limit development of the project site in a manner which is substantially in accordance with the plans which are to be voted on by the City Planning Commission pursuant to the Uniform Land Use Review Procedure (ULURP) including the provision of a public waterfront open space. The Restrictive Declaration will also provide for the implementation of specific conditions with respect to historic resources, the provision of new storm sewer outfalls at the end of 1st and 2nd Streets at the Gowanus Canal, re-grading of the project site, including 1st Street, to be above the 100-year base flood elevation, and the implementation of the requisite mitigation measures. In addition, measures related to the remediation of hazardous materials on the site would be implemented in accordance with a New York City Department of Environmental Protection (DEP)-approved Restrictive Declaration for the project site. With these measures in place, significant, adverse impacts related to hazardous materials would be avoided during and post construction.
The project site (the area the applicant seeks to redevelop), which totals about three acres (excluding streets), is currently occupied by warehouses, open vehicle storage, and vacant land and buildings. The applicant would redevelop this waterfront property with a predominantly residential development that would include market-rate and affordable housing with community facility and commercial space and accessory parking. In addition, the proposed project would provide approximately 0.7 acres of publicly-accessible waterfront open space on the Gowanus Canal along the entire project waterfront from 2nd Street on the south to Carroll Street on the north.
Page 2
Final EIS Notice of Completion 363-365 Bond Street, CEQR No.08DCP033K Under the proposed Special Mixed-Use District, the rezoning area would have a maximum floor area ratio (FAR) of 3.6 (with the provision of inclusion of 20 percent of the residential floor area as affordable housing for low-income households). This would allow a development program on the project site that would contain approximately 447 dwelling units (approximately 130 affordable), approximately 2,000 gross square feet (gsf) of community facility space, approximately 2,000 gsf of commercial space (providing commercial goods and services demands), and approximately 268 accessory parking spaces. The total size of the proposed project would be approximately 525,309 zoning square feet (zsf).
If the proposed actions are approved, it is expected that the proposed project would be completed in 2011.
B. DEVELOPMENT GOALS AND OBJECTIVES
The applicant is applying to CPC for discretionary actions that would allow for the redevelopment of a former waterfront industrial site along the Gowanus Canal with residential and other uses and a publicly-accessible waterfront open space. The proposed project would be a privately sponsored redevelopment project on the Gowanus Canal waterfront.
The project site, which is currently zoned for manufacturing use, comprises about three acres of mostly vacant or underutilized land that does not provide public access to the waterfront. The proposed project would redevelop this underutilized land with productive residential, community facility and commercial uses compatible with the surrounding area, including substantial publicly-accessible waterfront open space between 1st and 2nd Streets. The site layout and building configuration would be controlled through the proposed General Large Scale Development (GLSD) permit (see the discussion below). In addition, the mix of housing types would allow market-rate development while providing on-site affordable housing. The mix of uses would include on-site commercial (providing convenient goods and services within a short walking distance for local residents), and on-site community facility space (which the applicant expects will be occupied by the Gowanus Dredgers for equipment storage and community education). These uses would support the site’s waterfront location, attract local residents to the site’s proposed 0.7 acres of publicly-accessible waterfront open space and provide a recreational and aesthetic benefit for future project residents.
C. DESCRIPTION OF THE PROPOSED REZONING AREA AND PROJECT SITE
The area of the proposed rezoning is bounded by the midpoints of Carroll Street to the north, Bond Street to the west, 2nd Street to the south, and the Gowanus Canal to the east. The proposed rezoning area includes the project site (the area to be redeveloped) and the two City-owned outparcels. The outparcels contain a City EMS facility and infrastructure (the Operator’s House) associated with the Carroll Street Bridge.
The project site encompasses Brooklyn Tax Block 452 (Lots 1 and 15) and Tax Block 458 (Lot 1). The two blocks of the project site have a combined lot area of approximately 146,000 square feet and approximately 280 linear feet of frontage along Bond Street (excluding the bed of 1st Street), 48 linear feet of frontage along Carroll Street, 430 linear feet of frontage along 2nd Street, and 460 linear feet of frontage along the Gowanus Canal.
The two project blocks are currently zoned M2-1. The existing M2-1 zoning district is a medium-density manufacturing district. It allows industrial uses at a maximum FAR of 2.0 and includes performance standards; it does not allow residential use.
Page 3
Final EIS Notice of Completion 363-365 Bond Street, CEQR No.08DCP033K As shown in Table S-1, current uses on the project site include warehousing, open vehicle storage, vacant buildings. Existing buildings in the rezoning area and on the project site are primarily one- and two-story warehousing/industrial structures. The residential neighborhood of Carroll Gardens is directly to the west of the project site (across Bond Street). To the north and south, and along the east side of the Gowanus Canal, land uses are similar to those on the project site, with active and vacant industrial and mixed non-residential uses.
Table S-1Project Site Current Uses
Block Zoning Lot
(square feet)
Current Built square footage
(gsf) Stories Current Uses
Estimated No.
Employees
458 89,600 43,000 gsf (one building) 1
Storage/warehousing, truck parking/storage, surface
parking 10
452 56,400 46,000
(seven buildings) 1-3 Garment warehouse/distribution, 10
Source: AKRF field survey, January 2008.
D. PROPOSED ACTIONS
NEW YORK CITY PLANNING COMMISSION APPROVALS
In order for the proposed project to be developed, New York City Planning Commission (CPC) approval of the following discretionary actions is required:
• Zoning text amendment to: o Sections 123-63 and 123-90 to establish a Special Mixed-Use (MX) District in
Gowanus; o Sections 23-144, 23-922, and 23-942 to apply the Inclusionary Housing Program
to specified R7-2 districts; o Section 23-942 to apply standard height and setback regulations of MX districts
to developments utilizing the Inclusionary Housing Program in certain non-contextual MX districts;
• Amendment to the zoning map changing from an M2-1 district to an M1-4/R7-2 Special Mixed-Use District;
• Special permit pursuant to Section 74-743 to modify bulk regulations for height and setback (Section 123-662), inner court recesses (Section 23-852), and yards (Sections 23-45 and 123-651) in a general large-scale development.
To facilitate the redevelopment of the project site as proposed, the applicant is seeking zoning text amendments to Sections 123-63 and 123-90 of the Zoning Resolution. These text amendments (and related zoning map amendments) would establish a new mixed-use district that would appropriately reflect the uses proposed for the project, and reflect the mixed-use character of the surrounding neighborhood. As described above, the two project blocks are currently zoned M2-1. The proposed zoning district, Special Mixed-Use District M1-4/R7-2 (MX), would be mapped over the two-block area and allow a maximum floor-area ratio (FAR) of 3.6. R7-2 districts allow residential use at a maximum FAR of 3.4 and community facility uses at a maximum FAR of 6.5. The proposed M1-4 district is a manufacturing district that allows light industrial and certain commercial uses at a maximum FAR of 2.0.
Page 4
Final EIS Notice of Completion 363-365 Bond Street, CEQR No.08DCP033K As mentioned above, the two blocks of the project site have a combined lot area of approximately 146,000 square feet. The allowable zoning floor area (zfa) for the project site under the proposed rezoning would be approximately 525,309 zsf. This allowable floor area would be split between the two project blocks, with approximately 202,744 zsf on Block 452 (the northern block, proposed as 363 Bond Street) and approximately 322,565 zsf on Block 458 (the southern block, proposed as 365 Bond Street). The proposed zoning would allow the EMS facility and the Operator’s House (located within the area to be rezoned, but not within the area to be redeveloped) to remain within the rezoning area as conforming uses.
To facilitate the development of affordable housing on the site, the applicant is proposing amendments to sections 23-144, 23-922 and 23-942 of the Zoning Resolution to apply the Inclusionary Housing program and related floor area regulations to R7-2 zoning districts within the proposed special mixed use district. These amendments would add R7-2 districts within Community District 6 in Brooklyn to the list of residential districts in which the Inclusionary Housing Program would be applicable within certain designated areas, and would add the proposed Special Mixed-Use District (specified geographically), as one of the Inclusionary Housing designated districts. This would provide for a base FAR of 2.7 and a maximum FAR of 3.6 within the special mixed use district. Utilizing the bonus in FAR from 2.7 to 3.6, the proposed project would create approximately 447 new dwelling units, up to 130 of which would be permanently affordable for low-income households. Under the proposed project, consistent with City requirements, affordable housing for low-income households is defined as up to 80 percent of U.S. Department of Housing and Urban Development (HUD) income limits.
Since the proposed project seeks to participate in the Inclusionary Housing Program within special mixed use districts, the height and setback requirements of section 23-942 (b) (2) would apply to the development. The applicant proposes text amendments that would allow the development of the proposed market rate buildings to comply with the usual MX height and setback regulations within Section 123-662 for R7-2 districts mapped within special mixed-use districts. These would include a maximum base height of 60 feet, setbacks of 10 feet on a wide street and 15 feet on a narrow street, and a maximum building height of 135 feet.
A special permit to facilitate construction of the proposed buildings that do not strictly comply with the height and setback regulations contained within Sections 123-662, 23-852, 23-45 and 123-651 of the Zoning Resolution, will also be required, as follows:
• Section 123-662 ZR sets a maximum base height of 60 feet and maximum building height of 135 feet in R7-2 districts mapped within special mixed use districts. The buildings on the eastern portion of the site are proposed to have a maximum building height of 125 feet, 10 feet below the maximum permitted building height. However, the proposed base heights on the eastern street frontages of both Block 452 and Block 458 fronting on First Street and on Second Street are proposed to be 65 feet above the modified base plane, exceeding by 5 feet the maximum permitted base height within and R7-2 district (Section 123-662 ZR). The portions of the street walls for which a waiver is requested are 148.5 feet in length on Block 452 and 147.5 feet on the First Street frontage and 145 feet on the on the Second Street frontage of Block 458. The proposed maximum base height within these portions is 65 feet above the base plane.
• Inner court recesses must provide a minimum width to depth ratio of 2:1, pursuant to Section 23-852. However, in order to maximize the area of landscaped passive recreation area within each courtyard, one inner court recess with a width to depth ratio of 1:1 in each court is proposed. The proposed waiver will help to provide a superior residential amenity for the residents of the project.
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Final EIS Notice of Completion 363-365 Bond Street, CEQR No.08DCP033K
• Sections 23-45 and 123-651 require a minimum 30-foot deep rear yard for residential buildings unless they are corner lots or if the zoning lot comprises the entire block. Through lots are permitted to provide rear yard equivalents. Thus, there is no rear yard requirement for the proposed buildings on Block 458, as it comprises an entire City block. However, the development site on Block 452 is comprised of a corner lot, through lot and two interior lots. One of the interior lots (the eastern-most lot on this block) would not provide the required 30 foot rear yard due to the unusual block configuration caused by the city-owned parcel containing the bridge operator’s house and yard for the Carroll Street Bridge. Instead, a minimum 40-foot yard would be provided along the entire canal side.
OTHER CITY, STATE, AND FEDERAL APPROVALS
In addition to discretionary approvals from CPC, design approvals would be required from other City agencies, including DEP and the New York City Department of Transportation (NYCDOT). The New York City Department of Parks and Recreation (DPR) will also review and approve the open space design, layout, and furnishings.
Discretionary approvals from State and federal agencies, including DEC, and ACOE will also be required, since the project proposes the installation of a new sheet-pile bulkhead. The design, location and elevation of the proposed bulkhead are subject to the approval of DEC and ACOE. In addition, since the project proposes new outfalls to the Gowanus Canal (from 1st and 2nd Streets), and possible dewatering during construction, permits at the state level are expected to include tidal wetlands (if any bulkhead work is in water shallower than six feet), protection of waters, Long Island well permit (dewatering only), and a Stormwater Pollutant Discharge Elimination System (SPDES) permit for dewatering, construction (i.e., a stormwater pollution prevention plan [SWPPP] during construction and a stormwater outfall discharge from 1st and 2nd Streets).
When permits and approvals are required from State and federal agencies, these agencies are defined as involved agencies under City Environmental Quality Review (CEQR)/the State Environmental Quality Review Act (SEQRA). Therefore, as the lead agency, the New York City Department of City Planning (DCP) will provide a coordinated review of this EIS with the other involved agencies for the purposes of documenting consistent findings among the decision-making agencies.
E. PROPOSED DEVELOPMENT PROGRAM
PROPOSED USES AND BUILDING CONFIGURATIONS
The proposed actions would facilitate a proposal by the applicant to redevelop the entire site as proposed, with the new buildings and open space. The development program would result in a total of 602,603 gross square feet (gsf) including residential uses, community facility space, commercial space, and accessory parking (as required under zoning).
The proposed project would include three new building types on each block. The range of building heights would be from 4 to 12 stories (up to approximately 125 feet) with three principal design elements: (1) low-rise building components of approximately 60 feet (6 stories) fronting on Bond Street; (2) low-rise “townhouse” components of approximately 43 feet (4 stories) along the midblocks of 1st and 2nd Streets; and (3) low to mid-rise building components of 5 to 12 stories (up to 125 feet maximum) facing the waterfront open space. Each block would have an enclosed accessory parking garage for the use of its residents that would be located on the ground floor of the buildings. Table S-2 presents the approximate land coverage that would result on the project site with the proposed development.
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Final EIS Notice of Completion 363-365 Bond Street, CEQR No.08DCP033K
Table S-2Proposed Development Approximate Land Coverage (Excluding Streets)
Project Element Lot Coverage (square feet) Percent of Project Site Publicly-Accessible Open Space 23,165 16
Private Open Space 30,660 21 Pedestrian Access Easements 2, 559 2
4 story Building Elements (Townhouse-style buildings)
14, 715 10
5-6 story Building Elements 44,900 31 7-8 story Building Elements 16,265 11
11-12 story Building Elements 13,685 9 Total 145,949 100%
The residential component of the project would provide a total of 447 dwelling units, up to 130 of which would be reserved for low-income residents. Approximately 268 accessory parking spaces would be provided in two garages located on the ground floor of each block. As shown on the ground floor plan, the commercial space, totaling about 2,000 square feet, would be located along the south side of 1st Street, approximately 50 feet from the waterfront publicly accessible open space. The proposed commercial space would be easily accessible to pedestrians both on the street and on the waterfront open space. The applicant intends to locate a commercial use, such as a local deli or other such business providing local goods and services, in this space. The community facility space, also totaling about 2,000 square feet, would be located along the north side of 2nd Street. The applicant intends to provide this space to the Gowanus Dredgers (a local canoe and kayaking club), for equipment storage and community education. Under the proposed project, the access point to the canal (at the end of 2nd Street) that is currently used by the Gowanus Dredgers would remain, and would be incorporated into the new landscaped open space proposed for the end of 2nd Street.
In addition to the proposed new buildings, the proposed project would include a continuous, privately owned, publicly-accessible open space of approximately 23,165 square feet (about 0.5 acres) along the Gowanus Canal. In addition, approximately 7,656 square feet of landscaped open space at the street ends of 1st and 2nd Street would be provided, for a total of 30,821 (about 0.7 acres) of publicly accessible open space extending from Carroll Street on the north to 2nd Street on the south (as described below). Three pedestrian access easement areas totaling 2,559 square feet will also be provided on the project site along the cul-de-sacs at the street ends.
Principal pedestrian access to the proposed residential units would be from 1st Street and the corner of Bond and 1st Streets for both buildings. Vehicular access to the proposed accessory parking garages would be from 1st Street for both blocks.
The majority of the project site is mapped within a 100-year flood hazard zone. All buildings on the project site would comply with both Federal Emergency Management Agency (FEMA) and New York City Building Code requirements regulating construction within flood hazard areas. The applicant proposes to raise the elevations of portions of the project site to reduce the potential for flood damage or impacts on the proposed residential units. The lowest occupied floor elevation would be constructed approximately one foot above the 100-year base flood elevation. The site grade would then slope to match existing street grades along Carroll, Bond, and 2nd Streets. Street ends would also be designed in accordance with all City regulations, including those of the New York City Fire Department (FDNY) (see also the discussion under “Proposed Site and Infrastructure Improvements”).
Page 7
Final EIS Notice of Completion 363-365 Bond Street, CEQR No.08DCP033K PROPOSED OPEN SPACES
PUBLICLY-ACCESSIBLE OPEN SPACE
The proposed project would landscape and improve the entire waterfront along the eastern project site boundary for the purposes of providing public access from the south end of 2nd Street north to a connection with Carroll Street. Thus, the proposed project would improve and link the street ends of 1st and 2nd Streets with publicly-accessible waterfront open space at the two project blocks, approximately 600 linear feet long and a minimum of 40 feet wide.
In area, the proposed project would provide approximately 30,821 square feet (about 0.7 acres) of publicly-accessible open space along the Gowanus Canal waterfront (approximately 23,165 square feet of privately owned, publicly-accessible open space along the eastern border or the project site, connected seamlessly to approximately 7,656 square feet of public open space at the street ends of 1st and 2nd Streets). This open space would provide views along the waterfront as well as opening up new views of the historic Carroll Street Bridge, and would be landscaped with benches and other amenities for the purpose of providing publicly-accessible open space along this stretch of the Gowanus Canal waterfront. The proposed publicly-accessible open space would include planting areas, shade-providing trees, seating, lighting, pedestrian paths (which would be available for jogging and inline skating), a dog run, and other architectural features yet to be designed. A tidal wetland area would be created in the vicinity of the end of Second Street. As mentioned above, DPR will also review and approve the open space design, layout, and furnishings. Development on the site will be controlled pursuant to the special permit to substantially comply with the approved plans which will include the publicly accessible open space. The privately owned, publicly-accessible open space will be constructed, landscaped and maintained pursuant to a Restrictive Declaration that will be recorded for the project site, according to the approved plans. The open space would be managed and maintained by the proposed buildings’ homeowner’s associations. The hours of access are anticipated to be similar to those of City parks. Entrances to the open space would be at three locations, one at the north end (Carroll Street), one at the south end, (2nd Street) and another at the end of 1st Street.
As part of the design of the waterfront open space, the applicant intends to include industrial materials that are evocative of a particular place and time in the history of the development of the canal. This would also include a narrative ribbon that would thread through the handrails, telling the story of the Gowanus Canal, industrial Brooklyn and the legacy of environmental changes.
While the proposed paving materials are not subject to CPC approval, if possible, the applicant has stated that it would seek to either reuse the Belgian block from the pavement on the south sidewalk at the end of 1st Street and on the sidewalks and street at the end of Second Street (which is owned by the City of New York) on the project site’s streetscape or would encourage its salvage and reuse in another location.
In addition, the proposed project would landscape the end of 2nd Street and as part of that design would incorporate the existing access point to the water that is currently used by the Gowanus Dredgers. As described above, the proposed project would include community facility space that would be made available to the Gowanus Dredgers for equipment storage and community education.
PRIVATE OPEN SPACES
In accordance with the City’s Quality Housing provisions, the proposed project would also provide private courtyards within each building. Therefore, an approximately 11,600-square-foot courtyard would be provided in the 363 Bond Street building, and an approximately 19,000-
Page 8
Final EIS Notice of Completion 363-365 Bond Street, CEQR No.08DCP033K square-foot courtyard would be provided in the 365 Bond Street building. Both open spaces, currently un-designed, would provide outdoor recreational space for project residents.
PROPOSED SITE AND INFRASTRUCTURE IMPROVEMENTS
As stated above, in order to ensure that the proposed buildings would be above the 100-year floodplain, the project site would be graded to raise the base elevation above the local floodplain. All parking and occupiable space would then be constructed one foot above this base grade elevation.
In addition, with respect to site drainage and infrastructure, currently, all of the project site’s sanitary flow and a portion of the site’s stormwater flow from rooftops is conveyed to the Red Hook Water Pollution Control Plant (WPCP) via the combined sewer in Bond Street. The proposed project would eliminate site-generated stormwater flow from discharging to the combined sewer by installing new separate storm sewers in both 1st and 2nd Streets, with new stormwater outfalls to the Gowanus Canal. These new storm sewers would be designed in accordance with DEP standards. This separation of stormwater would remove the project site's stormwater from the local combined sewer system. The proposed project would also install new catch basins on the west side of the intersection of Bond and 1st Streets, thereby improving local drainage conditions. Stormwater from the project blocks would also be treated through the use of hydrodynamic separators that would remove grease, solid and floatables prior to discharge into the canal. The proposed project would also detain stormwater in the planted interior courtyards, supporting the proposed vegetation. There would also be open tree pits along the streets and planted strips along the waterfront where rainwater would infiltrate to the ground below. Lastly, the street drainage to the canal, in accordance with DEP design, would be provided with DEP standard Type II catch basins with a sump and hood that would prevent solids and floatables from being discharged into the canal.
All sanitary flow from the proposed project would be separately conveyed to the Red Hook WPCP for treatment via the existing combined sewer in Bond Street.
PROPOSED WATERFRONT OPEN SPACE AND BULKHEAD IMPROVEMENTS
Currently, the bulkhead along the project site is a timber crib design that, though currently functioning, could not be utilized or repaired for the purposes of meeting the proposed waterfront access goals of both the project and the City. Therefore, in order to improve the water’s edge to provide waterfront open space, the proposed project would modify the existing infrastructure by installing a new steel sheet pile bulkhead for the entire length of the waterfront. The design, location and elevation of the proposed bulkhead are subject to the approval of DEC and ACOE. Where portions of the existing bulkhead are currently overtopped during high tide events, the existing elevation of the bulkhead may be maintained and an intertidal area may be created landward of the new bulkhead, if required by DEC and/or ACOE. The new bulkhead would either be placed in the same footprint as the existing bulkhead or would be placed against the face of the existing timber crib bulkhead, subject to the approval of DEC and/or ACOE. The preferred design is to place the sheet steel against the face of the existing timber crib bulkhead as it would:
• Avoid the release of upland contaminants into the canal during construction, • Avoid the release of sediments into the canal, • Minimize the disturbance to the waterfront and canal to the greatest extent possible, • Facilitate the most efficient installation of the new bulkhead, • Preserve to the greatest extent possible the State/National Register of Historic Places
(S/NR)-eligible timber bulkhead and crib system, and
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Final EIS Notice of Completion 363-365 Bond Street, CEQR No.08DCP033K
• Shorten the duration of construction along the shoreline edge, thereby minimizing potential impacts.
The preferred design would require the removal of existing whalers and piles from the existing timber crib bulkhead. In addition, for any new installation an anchoring system consisting of “deadmen” and steel “tie rods” would be installed upland below-grade, and inland of the existing crib (or approximately 40 feet upland). The tie rods would run from the new sheeting to the deadmen approximately every eight feet for the length of the bulkhead. The installation of the tie rods would require four to five foot deep trenches. The installation of the tie rods could potentially require removal of portions of the crib sufficient to allow the steel tie rods to pass through the area. The proposed bulkhead would have a boat fender system on its seaward face. This would be constructed of wood to mimic existing conditions along the canal.
These proposed waterfront infrastructure improvements would impact an historic resource, the Gowanus Canal bulkhead, which the State Historic Preservation Office (SHPO) has determined eligible for listing on the State/National Register of Historic Places as both an archaeological and architectural resource. In order to mitigate impacts to the bulkhead, the reconstructed bulkhead would be faced in wood to match the existing face. In addition, a mitigation plan has been developed to document and recover archaeological information relative to the bulkhead within the area to be disturbed during construction (see “Mitigation,” below).
F. FRAMEWORK FOR ANALYSIS
The environmental review presented in this DEIS examines impacts of a site-specific rezoning and development proposal. It includes the rezoning of the site from M2-1 to M1-4/R7-2 (MX) thereby allowing the development of the proposed project with approximately 447 dwelling units (of which up to 130 would be affordable housing units), commercial space (approximately 2,000 square feet), community facility (approximately 2,000 square feet), and 268 accessory parking spaces.
If approved, the proposed project would also be developed under a GLSD. As a result, the design of the buildings and the open space must be developed in accordance with the special permit that is necessary for the proposed project to move forward. Thus, unlike a proposal that contains only a zoning action, the site-specific development of the proposed project is examined within this DEIS. In addition, as stated above, Restrictive Declarations would be used to implement measures such as hazardous materials cleanup. Thus, in addition to being a zoning action, the proposed project is a site-specific development proposal which significantly defines the project for analysis within this DEIS. Additionally, the project requires State and Federal approvals for improvements along the water’s edge and new outfalls that will be subject to future site-specific engineering designs. These designs are conceptually presented in this DEIS.
The project build year is 2011, which is the year in which it is expected that the proposed project would be occupied.
CEQR requires a comprehensive analysis of proposed actions or projects in the context of other proposals. Thus, the impacts of this project are not measured against currently existing conditions, but are assessed based on the impacts of the project at the time of occupancy and the completion of construction. To assess conditions in the future without the proposed project (“No Build” conditions), the DEIS typically includes known or approved development proposals and other actions that may also be pending (and under environmental review) where the development is expected to occur on or before the occupancy of the proposed project (or 2011 in this case). The conditions in that 2011 No Build analysis year are then projected based on changes in housing and population (for example), and also take into account growth factors (such as traffic)
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Final EIS Notice of Completion 363-365 Bond Street, CEQR No.08DCP033K and projections from other City agencies (e.g., projected changes in student enrollment). In addition, given that DEP has a major capital improvement proposed at the head of the canal (i.e., the upgrade of the Gowanus pump station and Flushing Tunnel), infrastructure and natural resources conditions have also been assessed in this DEIS for the year 2013, which is after the project’s build year. This analysis was also performed in response to comments and for the purposes of analyzing environmental conditions, with the proposed project in place as well as these major capital improvements.
The projection of conditions through 2011 is also based on a study area that has been identified for each technical analysis. In many cases, these study areas have been expanded in response to public comments received through the scoping process for the EIS.
Impacts of the proposed project in the analysis year (“Build” conditions) are then measured against the “No Build” conditions in order to determine the incremental impacts of the proposed project and the levels of impact significance based on the guidelines of the CEQR Technical Manual.
Currently, the New York City Department of City Planning Commission is considering an areawide rezoning for the Gowanus Canal area. This draft rezoning proposal was presented to the public at a public meeting of the Community Board 6 Land Use Committee on May 29th, 2008 (this proposal was previously presented as a Gowanus Canal Corridor Framework by DCP). In the forthcoming months, the draft rezoning proposal will be refined and is expected to be released formally in a Draft Scope of Work for the purposes of preparing a Draft Environmental Impact Statement on the proposed areawide rezoning in early 2009. That Scope of Work will include a Reasonable Worst Case Development Scenario that will identify projected and potential sites that could be developed under the DCP area-wide rezoning proposal.
G. PROBABLE IMPACTS OF THE PROPOSED PROJECT
LAND USE, ZONING, AND PUBLIC POLICY
The proposed project would allow the project site to be redeveloped with a predominantly residential development that would include market-rate and affordable housing with community facility and commercial space and accessory parking. In addition, the proposed project would also provide approximately 0.7 acres of publicly-accessible waterfront open space on the Gowanus Canal along the entire project waterfront from 2nd Street on the south to Carroll Street on the north. The City-owned parcels in the rezoning area would not be redeveloped as a result of the proposed projects. As described below, this analysis concludes that the proposed project would be consistent with surrounding uses and existing neighborhood trends, and as such would have no significant adverse impacts on land use, zoning, or public policy in the study area. In addition, the proposed project would promote the objectives of and be consistent with the goals of public policy initiatives that affect the project site. Specifically, the proposed project would be consistent with the applicable initiatives and goals described in PlaNYC.
SOCIOECONOMIC CONDITIONS
The socioeconomic analysis concludes that the proposed project would not have a significant adverse impact on socioeconomic conditions in the study area. The introduction of residential units, community facility and commercial uses, and accessory parking as planned under the proposed project would have no significant direct or indirect adverse impacts on population, housing stock, or economic activities in the local study area, nor would it adversely affect regional economic conditions of a specific industry.
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Final EIS Notice of Completion 363-365 Bond Street, CEQR No.08DCP033K COMMUNITY FACILITIES
Overall, the proposed project would not have significant adverse impacts on community facilities. This accounts for updated generation rates for day care and schools published since the date of the DEIS. The proposed project would not generate a population large enough to impact libraries or health facilities; nor would it directly or indirectly impact police services or fire services or facilities. The schools analysis concludes that even with the student-age population generated by the proposed project, there would be sufficient capacity in the local public schools to accommodate this added demand. The day care analysis estimates that the proposed project would generate approximately 69 children under the age of 6 who would be eligible for publicly funded day care programs, and approximately 25 children between the age of 6 and 12 who would be eligible for publicly funded after school day care programs. Even with these additional eligible children, day care facilities within 1 mile of the project would remain below capacity with available slots. Therefore, the proposed project would not result in significant adverse community facility impacts on schools or day care facilities.
OPEN SPACE
The proposed project would not result in any significant adverse open space impacts. The proposed project would introduce new residents, but would also create approximately 0.7 acres of new waterfront open space along the canal. As a result, passive open space ratios would increase slightly in the future with the proposed project, and the total residential open space ratio would remain the same. The active open space ratio would decrease by 3 percent. However, because the study area has a low active open space ratio, other factors must be considered to demonstrate that even this small decrease in the active open space ratio does not result in a significant adverse impact.
In this instance, a number of factors demonstrate that although the study area has a low active open space ratio and this ratio would decrease with the proposed project, this decrease would not constitute a significant adverse impact. First, it is recognized that the DCP guidelines for active open spaces are not attainable in many areas of the city, and are not considered impact thresholds. Moreover, the quantitative effects of the proposed project on the active open space ratio would be very limited; the ratio would decrease by only 0.01 acres per 1,000 people with the proposed project.
Finally, the quantitative analysis does not account for the approximately 66.77 acres of mostly active open space in Red Hook Park and the Red Hook Recreation Area, which are located just outside of the study area. It is likely that residents of the proposed project would make use of this significant recreational space (which includes athletic facilities such as soccer and softball fields), thus allaying the shortage of active open space predicted by the quantitative analysis. In addition, the proposed 0.7-acre publicly-accessible open space along the canal was considered entirely passive in the quantitative portion of this analysis, but active recreation such as jogging or cycling would be allowed within the publicly accessible open space, and would be expected to occur, especially if similar amenities are built along other portions of the canal beyond the proposed project’s 2011 Build year. The proposed project would also include private residential amenity space such as an accessory gym and private open spaces in building courtyards for its residents. These private amenities would likely serve to reduce the impact of the project’s residents on active open spaces in the study area. Therefore, the proposed project would not result in a significant adverse impact on active or passive open space in the study area.
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Final EIS Notice of Completion 363-365 Bond Street, CEQR No.08DCP033K SHADOWS
The proposed project would not result in significant adverse shadow impacts on any existing publicly-accessible open spaces, sun-sensitive features of nearby historic resources or important natural features.
HISTORIC RESOURCES
ARCHAEOLOGICAL RESOURCES
The proposed project would construct a new steel sheet pile bulkhead along the length of the eastern boundary of the project site either in place of or outside of the existing, archaeologically sensitive bulkhead to make possible the construction of the proposed waterfront open space along the canal. The installation of the new bulkhead could require removal of portions of the existing one. In addition, two new stormwater outfalls would be constructed through the existing bulkhead—one at the end of 1st Street and the other at the end of 2nd Street. LPC has determined that the bulkhead rehabilitation work and storm water outfall installation would adversely impact portions of the bulkhead at the project site. Therefore, an archaeological field investigation would be undertaken in coordination with LPC that would document the extent and significant characteristics of the Gowanus Canal bulkhead. This archaeological documentation would serve as mitigation of the adverse impact to the bulkhead under CEQR. This field investigation would occur either in advance of or in concert with the bulkhead reconstruction and storm water outfall installation. An Archaeological Testing Protocol in compliance with the LPC Guidelines for Archaeological Work in New York City would be prepared and implemented in coordination with LPC. In addition, as requested by SHPO, an Unanticipated Discovery Plan for both human and non-human remains would be prepared in consultation with SHPO and implemented during project-related construction at the site.
ARCHITECTURAL RESOURCES
Project Site All of the buildings on the project site would be demolished under the proposed project. None of the buildings that would be demolished are considered contributing elements within the S/NR-eligible Gowanus Canal Historic District. As noted above, the proposed project would rehabilitate the Gowanus Canal bulkhead. It is anticipated that the reconstructed bulkhead would be faced in wood to match the existing bulkhead. To avoid adverse effects on the historic character of the bulkhead, the project sponsors would consult with SHPO on the designs of the new bulkhead, including submitting plans for the rehabilitation to SHPO at the preliminary and pre-final design stages.
Primary Study Area The Carroll Street Bridge and Operator’s House (S/NR-eligible; NYCL) is an architectural resource located within 90 feet of projected construction activities. To avoid any construction-related impacts to this resource, a Construction Protection Plan (CPP) would be developed and implemented in consultation with LPC, SHPO, and NYCDOT prior to project demolition and construction activities. No other architectural resources are located close enough to the project site to experience potential construction-period impacts.
The proposed project would somewhat alter the context of the Carroll Street Bridge in that it would involve the demolition of industrial buildings adjacent to the resource and the construction of a taller residential complex on the site. However, the Carroll Street Bridge is significant primarily for its unique engineering, which significance would not be affected by the proposed project. Therefore, the proposed project would not impact the qualities that qualify it for NYCL
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Final EIS Notice of Completion 363-365 Bond Street, CEQR No.08DCP033K status or S/NR eligibility. An engineering study has determined that no cumulative adverse impacts on the bridge would result from projected traffic increases associated with the proposed project. In addition, the proposed project would create new public access to and along the Gowanus Canal including an esplanade and plaza area adjacent to the Carroll Street Bridge. This amenity would be expected to improve access to, and the visibility of, the Carroll Street Bridge. Therefore, the proposed project is not expected to have an adverse impact on the Carroll Street Bridge.
Two features that contribute to the S/NR-eligible Gowanus Canal Historic District are located within the project’s 400-foot study area: the Former BRT Power House (located across the canal, roughly 300 feet east of the project site), and the Gowanus Canal Waterway (which runs immediately adjacent to the project site). While the context of the Power House and the Waterway would change somewhat with the construction of the project, this change would not constitute a significant adverse impact. Furthermore, the proposed masonry and glass buildings have been designed to complement the character of the nearby residential district. The SHPO has determined that the proposed project would have no adverse effect on the S/NR-eligible Gowanus Canal Historic District provided that proposed landscape plans for the portion of the project site along the canal are submitted to SHPO for review and comment at preliminary and pre-final design stages.
With the proposed project, the context of the 59-97 Second Street rowhouse block, determined National Register-eligible as part of this project and located roughly 150 feet west of the project site, would also be somewhat altered by the addition of a modern residential complex nearby. However, views from the potential historic rowblock to the project site are limited, because views from the rowhouse block are generally oriented south, while the project site is located to the northeast. Furthermore, the portions of the proposed project located closest to the potential historic resource would be low-rise while the taller, mid-rise components would be located farther away. Therefore, no significant adverse contextual impacts to the potential historic resource would occur.
Secondary Study Area The Carroll Gardens Historic District is located in the secondary study, roughly 500 feet west of the project site. Views to the project site from the Carroll Gardens Historic District are extremely limited due to the relatively long distance to the project site, the presence of intervening buildings, and the street orientation. Furthermore, the project buildings have been designed with low-rise elements in the western portion of the project site (the portion closest to the Carroll Gardens Historic District) and the medium-rise elements further east, thus further minimizing any views of the project buildings that may be available from the Carroll Gardens Historic District. Therefore, the proposed project would not substantially alter the context or visual character of the Carroll Gardens Historic District, and would have no adverse impact on the resource. Therefore, the proposed project would not substantially alter the context or visual character of the Carroll Gardens Historic District, and would have no adverse impact on this resource.
Other known and potential architectural resources are located in the secondary study area. These are situated relatively far (between roughly 450 feet and ½ mile) from the project site and therefore would not be directly impacted by the proposed project. In terms of potential indirect impacts, current views to the project site from the architectural resources in the secondary study area are either limited or nonexistent. No important views to or from the architectural resources in the secondary study area would be blocked as a result of the proposed project. Therefore, no adverse impacts to architectural resources in the secondary study area would result from the proposed project.
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Final EIS Notice of Completion 363-365 Bond Street, CEQR No.08DCP033K URBAN DESIGN AND VISUAL RESOURCES
This analysis concludes that the proposed project would not have a significant adverse impact on urban design and visual resources. Although changes would occur, the proposed project would substantially improve the condition of the project site and create new waterfront access for the neighborhood. The proposed residential buildings would be taller and have a greater footprint than the existing buildings on the site. However, these changes would not have a significant adverse impact on urban design or on the overall visibility of visual resources from public spaces within the study areas. The proposed project has been designed to maintain as much as possible the low-rise character of the nearby blocks and to blend with the streetscapes of surrounding neighborhood. The proposed project is expected to enhance the overall vitality of the surrounding streets by introducing residential uses and a waterfront esplanade from which the public would be afforded an improved view of many visual resources, including the canal itself. Therefore, the proposed project would reflect a reasonable balance between existing and proposed building heights, and bulk and new open space without causing any significant adverse impacts.
NEIGHBORHOOD CHARACTER
The analysis concludes that the proposed project would not have a significant change in neighborhood character with respect to land use, urban design and visual resources, historic resources, socioeconomic conditions, traffic and pedestrians and noise. Therefore, the proposed project would not have a significant adverse impact on neighborhood character. The proposed project would contain new market rate and affordable housing with supporting commercial and community facility uses and publicly-accessible open space, extending the residential character of nearby residential neighborhoods eastward onto the two project blocks. The proposed project has been designed to maintain as much as possible, the low-rise character of the project blocks, and to blend with the streetscapes of surrounding neighborhood. The existing one- to two-story buildings on the project site would be replaced with six-story building components along Bond Street, four-story townhouse components in the mid-block sections, and medium-rise components located further east on the project site. By distributing the respective building heights in this manner, Bond Street’s low-rise character would be maintained. The proposed buildings would be subject to the quality design requirements of a general large-scale development plan to ensure that the design of the proposed structures would not conflict with the neighborhood. It would also meet the Quality Housing Provision of the City. The proposed project would provide much needed local housing, both market rate and affordable, meeting the City’s objectives of maintaining a mix of housing types in the local community. Community facility space and amenities would also be provided for the local neighborhood. In addition, the proposed project would introduce a new publicly-accessible landscaped waterfront esplanade (approximately 0.7 acres) from which the public would be afforded an improved view of many visual and historic resources, including the historic Carroll Street Bridge, the Former Brooklyn Transit Power House, the canal itself and its bulkheads. This would be the first such open space along this stretch of the canal. While there would be increased pedestrian and vehicular activity on local streets, these increases would not be expected to significantly affect any of the neighborhoods in the study area. Any projected traffic impacts would be mitigated. In addition, any impacts to the on-site bulkheads would be mitigated through an archaeological investigation that would have the potential to yield knowledge as to the historical methods used in developing the canal. It is anticipated that the reconstructed bulkhead would be faced in wood to match the existing, and the project sponsors would coordinate the design with SHPO to ensure that the bulkhead design is in keeping with the historic character. The redevelopment of the two blocks would also provide for the environmental cleanup of the site.
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Final EIS Notice of Completion 363-365 Bond Street, CEQR No.08DCP033K NATURAL RESOURCES
GROUNDWATER
The proposed project would not result in any significant adverse impacts on groundwater including groundwater conditions, flow or quality. Rather, “Hazardous Materials,” as part of the remediation of the project site prior to construction, the proposed project would remove on-site sources of groundwater contamination, thus providing a benefit with respect to local groundwater quality. In addition, the proposed bulkhead would have more than enough capacity to accommodate the projected flow of groundwater from stormwater recharge on the project site. Therefore, it can be concluded that the proposed project would not adversely impact groundwater conditions along the canal or in the surrounding area.
WETLANDS
The proposed project would install approximately 555 linear feet of steel sheet pile bulkhead either in place of or against the existing timber sheathing along the Gowanus Canal. An intertidal area in the vicinity of the end of 2nd Street where the canal overtops the bulkhead would, subject to DEC and ACOE approval, be maintained and upgraded. Installation of the new sheet pile bulkhead may result in minimal loss (i.e., approximately 300 square feet) of DEC littoral zone tidal wetlands that may be located within the footprint of the new bulkhead. Therefore, a de minimis impact on littoral zone wetlands would occur as a result of bulkhead installation. This impact would be minimized to the extent possible through the implementation of measures identified during the permitting process for these shoreline improvements by federal and state agencies. This de minimis impact would not be considered a significant impact on tidal wetlands that would require mitigation. In addition, any de minimis filling would be offset by the creation of a tidal wetland area of the same square footage and transitional plantings in the vicinity of the end of 2nd Street).
TERRESTRIAL RESOURCES
No significant adverse impacts would occur with respect to terrestrial resources. Currently, the project site is 95 percent impervious surface cover with scattered invasive plants indicative of disturbed conditions. The construction of the proposed project would create approximately 0.7 acres of waterfront open space that would be planted with a variety of native and ornamental trees, shrubs, grasses, and herbaceous perennials. More than 30 trees would be planted including American redbud (Cercis Canadensis), oaks (Quercus spp.), and beech (Fagus spp.) (the applicant will consult with the New York City Department of Parks and Recreation (DPR) to ensure that all street tree and publicly-accessible open space tree species planted on-site are appropriate for the project area and are not known Asian Longhorn Beetle (ALB) host species). This habitat enhancement along the water’s edge would provide potential habitat for common songbirds, small mammals, and pollen-dependent species (e.g., honeybee and butterfly species).
AQUATIC RESOURCES
Water Quality Currently, approximately one-third of the project site’s stormwater runoff is untreated and discharged to the combined sewer in Bond Street. Under the proposed project, no stormwater from the project site would be discharged to this combined sewer and all stormwater from the two project blocks would be collected, treated, and discharged to new storm sewers to be constructed beneath 1st and 2nd Streets, which would then outlet into the Gowanus Canal. Stormwater pollutant loads from the project site would be reduced in the proposed project condition due to the conversion of industrial uses and existing paved surfaces to residential uses and proposed
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Final EIS Notice of Completion 363-365 Bond Street, CEQR No.08DCP033K landscaped areas, the latter of which would also reduce the amount of total runoff from the project site. With the proposed project relative to site-generated runoff, there would be a reduction in existing pollutant loads to the canal of approximately 21 percent of biochemical oxygen demand (BOD), 44 percent of the total phosphorus, 47 percent of the total nitrogen, and 38 percent of total suspended solids (TSS). Stormwater would be treated through the use of best management practices (BMPs). Therefore, the proposed project is expected to improve water quality conditions near the project site with the resulting benefits for aquatic biota. In addition, the proposed project would not result in significant adverse impacts on CSO flow, and the number of CSO events in the downstream combined sewer system, and therefore would not adversely impact the water quality of the canal. Water quality modeling results show the proposed project would not result in any water quality impacts on the Gowanus Canal for principal water quality parameters such as dissolved oxygen and pathogens.
Aquatic Biota The installation of the steel sheet pile bulkhead either in place of or against the existing timber sheathing has the potential to result in short-term construction related impacts to water quality and aquatic biota that would not be significant. These impacts may include localized increases in suspended sediment and re-suspension of contaminated sediments, temporary loss of fish habitat, and a de minimis disturbance to benthic communities during the installation of the existing shoreline stabilization features. Because the increase in suspended sediment would be localized and temporary, no significant adverse impacts would occur to aquatic biota. The loss of some benthic habitat and some macroinvertebrates during the removal of portions of the existing timber bulkhead and installation of the new bulkhead would not result in significant adverse impacts to populations of macroinvertebrates, as limited populations have been observed using this portion of the Gowanus Canal, nor would it significantly impact the food supply for fish foraging in the area. Encrusting organisms and benthic macroinvertebrates would be expected to recolonize the new bulkhead shortly after construction is completed. In addition, based on water quality modeling results, no significant adverse impacts to water quality are expected, and therefore no residual or secondary impacts on aquatic resources would occur. It should be noted however, that although not significant, the impacts associated with an in-place replacement of the bulkhead would be greater than with the preferred design (new sheet pile placed against the existing timber sheathing).
ENDANGERED, THREATENED, AND SPECIAL CONCERN SPECIES
No threatened, endangered, or special concern species have been identified on or in the immediate vicinity of the project site. Therefore, no significant adverse impacts to threatened or endangered species or special concern species would occur as a result of the proposed project.
ESSENTIAL FISH HABITAT
No significant adverse impacts on fish listed by the National Marine Fisheries Service (NMFS) as having essential fish habitat (EFH) for this area would result from the proposed project.
HAZARDOUS MATERIALS
Construction at the project site would entail demolition of the existing buildings on the project site, raising the existing elevation by approximately 0 to 6 feet depending on site topography, and subsequent construction of new foundations. Prior to or as part of any new construction at the project site, the project sponsor would undertake the following actions:
• Any drums, chemicals, and remaining equipment would be removed and disposed of off-site in accordance with all applicable regulations.
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Final EIS Notice of Completion 363-365 Bond Street, CEQR No.08DCP033K
• Demolition of the existing structures would be in accordance with applicable federal, state, and City requirements relating to asbestos, lead paint and disposal of solid waste.
• Any found Underground Storage Tanks (USTs) and existing Aboveground Storage Tanks (ASTs) would be registered with DEC, then removed in accordance with DEC requirements.
• Any excavated soils and fill materials would be removed from the site and properly disposed of in accordance with all applicable DEC regulations and at an appropriate disposal facility.
All subsurface soil disturbance would be performed in accordance with a RAP/CHASP. The RAP would provide for the appropriate handling, stockpiling, testing, transportation and disposal of these materials in accordance with all applicable federal, state and local regulations. The CHASP would ensure that all such work is done in a manner protective of both human health and the environment. The RAP/CHASP was approved by the New York City Department of Environmental Protection (DEP) on January 29, 2009. These measures will be implemented in accordance with a DEP-approved Restrictive Declaration for the project site. Further, with respect to active spill numbers, the remediation would also be undertaken in consultation with DEC.
With these measures in place, significant adverse impacts related to hazardous materials would be avoided during and post construction.
WATERFRONT REVITALIZATION PROGRAM
Because the proposed project is located within the City’s Coastal Zone, it is subject to the policies of the New York City Waterfront Revitalization Program (WRP), which establishes the City’s policies for development and use of the waterfront and provides a framework for evaluating activities proposed in the Coastal Zone. The proposed project would be consistent with the City’s 10 WRP policies and standards. It would encourage greater public use of the coastal zone and improve water quality through the elimination of currently uncontrolled pollutant flows into the Gowanus Canal.
INFRASTRUCTURE
The proposed project would not result in any significant adverse impacts related to infrastructure.
WATER SUPPLY
Water demands of the proposed project would not overburden the City’s water supply system. Based on the CEQR Technical Manual, the incremental 114,032 gallons per day (gpd) of water supply demand from the proposed project would not adversely affect the capacity of the City’s water supply system in providing water to the proposed project site nor would it impact water pressure for local users. Moreover, project-specific calculations developed by the applicant have disclosed that with the use of low flow fixtures the actual water demand rate would be much less than that projected under the CEQR Technical Manual, or 56,200 gpd, about half of the CEQR rates.
SANITARY SEWAGE
The Red Hook WPCP currently handles approximately 33 million gallons per day (mgd) of sewage flow and is designed to treat a dry weather flow of 60 mgd. Based on the CEQR Technical Manual, the added sanitary sewage discharge of approximately 114,032 gallons per day (gpd) resulting from the proposed project represents approximately 0.4 percent of the current 33 mgd of flow handled by the Red Hook WPCP. Thus, the projected increase in sanitary sewage resulting from the proposed project would not cause the Red Hook WPCP to exceed its
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Final EIS Notice of Completion 363-365 Bond Street, CEQR No.08DCP033K operational capacity or the New York State Pollution Discharge Elimination System (SPDES) permitted capacity of 60 mgd. In addition, as stated above, project-specific calculations developed by the applicant have disclosed that with the use of low flow fixtures the actual water demand rate would be much less than that projected under the CEQR Technical Manual, or 56,200 gpd, about half of the sanitary wastewater rates used in this conservative impact analysis using CEQR rates.
STORMWATER
Currently, approximately one-third of the project site’s stormwater runoff is discharged to the combined sewer in Bond Street. Under the proposed project, two new stormwater sewers would be installed (one at 1st Street and one at 2nd Street) that would convey all site-generated stormwater to the Gowanus Canal via two new storm sewer outfalls also to be constructed as part of the proposed project. Both of these new outfalls would require a SPDES permit from the DEC. In addition, to meet DEC requirements, the proposed project would provide pre-treatment for all stormwater collected from the two project blocks, prior to discharge to the storm sewers. This aspect of the project would eliminate any storm flows from the project site reaching the Bond Street combined sewer. Thus, with the proposed project, the project site would not contribute any stormwater flows to the combined sewer or to combined sewer overflow (CSO) discharges to the canal (see the discussion below). In addition to removing stormwater from the project site, the project also proposes to redirect stormwater runoff from the street in the area around Bond Street at 1st Street away from the combined sewers by providing drainage inlets at this location and connecting these inlets to the proposed new storm sewer to be built in 1st Street. The redirection of this additional stormwater runoff would improve conditions relative to local street flooding at this location.
COMBINED SEWER OVERFLOW (CSO) AND WATER QUALITY
An engineering modeling analysis was undertaken of the potential for the proposed project to affect CSO conditions along the Gowanus Canal. The nearest downstream combined sewer overflow location (CSO) from the project site is identified as RH-035 and is located at 4th and Bond Streets. As stated above, based on the CEQR Technical Manual, sanitary sewage generated by the project site would increase by approximately 114,032 gpd or 0.18 cubic feet per second (cfs) with the proposed project. This flow would be directed to the Bond Street combined sewer. However, as described above, the proposed project would also modify current stormwater flow patterns at the site by installing new storm sewers and creating new buildings and open spaces. As a result, with the proposed project, stormwater runoff from the project site would be conveyed through two new storm sewers that would outlet to the Gowanus Canal. In addition, with the treatment of the separated project stormwater runoff, a reduction in pollutant loadings from the project site to the Gowanus Canal would occur, providing a benefit for the water quality of the canal.
Based on infrastructure and water quality modeling using both CEQR Technical Manual sanitary flow rate calculations (approximately 114,032 gpd) and actual project-specific sanitary flow rates (56,200 gpd, about half of the CEQR-calculated rates), the following conclusions can be made:
• The proposed project would not result in any increase in the number of annual CSO events that are projected to occur in the canal in 2011 (73 total events).
• In 2011, assuming the CEQR Technical Manual sanitary flow rate calculations for the proposed project, there would be a very limited projected increase in CSO volume to the canal (over the 2011 No Build condition) of approximately 0.8 MG/yr (or 0.2 percent of the total CSO discharge to the canal).
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Final EIS Notice of Completion 363-365 Bond Street, CEQR No.08DCP033K
• In 2011, assuming the project-specific sanitary flow rates (which incorporates actual design features such as low-flow fixtures), there is a limited projected decrease in CSO volume to the canal over the course of the year, of approximately 100,000 gallons annually.
• In no scenario would the proposed project result in any water quality impacts on the Gowanus Canal for principal water quality parameters such as dissolved oxygen and pathogens.
In 2013, proposed DEP improvements at the Gowanus Pump Station and the Gowanus Flushing Tunnel are scheduled to be completed. Once in place, these upgrades would significantly improve the water quality of the canal and also reduce the impact of the proposed project on CSO volumes. The improvements at the pump station would reroute flow directly to the Columbia Street Interceptor via a new force main, thereby relieving the Bond Street sewer, thus reducing the CSO discharges to the canal by eliminating the use of Bond Street combined sewer as a bypass. These actions would reduce the impact of the incremental sanitary flow contribution from the proposed project resulting in an overall reduction in the CSO volume. In addition, the upgrade and restoration of the Gowanus Flushing Tunnel would improve circulation through the canal. Both of these DEP capital improvement projects would improve the water quality of the Gowanus Canal and the proposed project would not adversely affect the water quality benefits that are projected with these system upgrades. Additional modeling results show that:
• The proposed project would not result in any increase in the number of CSO events that are projected to occur in the canal in 2013 with the proposed Gowanus Pump Station improvements in place (33 total events).
• In 2013 (with the Gowanus Pump Station and Gowanus Flushing Tunnel upgrades in place), assuming the CEQR Technical Manual sanitary flow rate calculations for the proposed project, the proposed project would result a projected decrease in CSO volumes of 0.1 MG discharged to the canal over the course of the year.
• In 2013 (with the Gowanus Pump Station and Gowanus Flushing Tunnel upgrades in place), assuming the project-specific sanitary flow rates, there would be a reduction in CSO volumes of 0.1 MG discharged to the canal over the course of the year. See Appendix C, Table 1.
SOLID WASTE AND SANITATION SERVICES
The proposed project would result in a net increase over existing conditions of approximately 1.12 tons of solid waste per day in 2011. Although the proposed project would create new demand for the disposal of solid waste, municipal and private solid waste services would have adequate capacity to meet these increases in demand. Therefore, the proposed project would not result in any significant adverse impacts on solid waste and sanitation services.
ENERGY
The proposed project would result in added energy demand of approximately 78,480 million British Thermal Units (BTUs), which would constitute less than 0.02 percent of the total peak energy demand for New York City in 2011, and is not considered to be significant. Therefore, the energy demand from the proposed project would be met and the proposed project would not result in any significant adverse impacts on energy systems.
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Final EIS Notice of Completion 363-365 Bond Street, CEQR No.08DCP033K TRAFFIC AND PARKING
TRAFFIC
For the streets around the site, future intersection volumes would generally represent an increase over the existing traffic volumes, and the street capacities at majority of the locations would be sufficient to accommodate these increases.
Based on the CEQR standards, the proposed project could result in significant impacts at the following two signalized intersection approaches:
• The eastbound approach of Carroll Street at 3rd Avenue during the AM and PM peak hours; and
• The eastbound approach of Carroll Street at 4th Avenue during the AM and PM peak hours.
The eastbound approach of Carroll Street at 3rd and 4th Avenues operates at congested levels (Level of Service [LOS] F) during both the AM and PM peak hours in the No Build conditions. With the proposed project in place, the moderate increase in traffic levels (up to 38 vehicles during any given peak hour) at the eastbound Carroll Street approach at 3rd Avenue and 4th Avenue would result in significant traffic impacts.
While the delay at the eastbound approach of 1st Street at Bond Street would also increase significantly during the AM peak hour (from 18.7 seconds in the No Build conditions to 48.8 seconds in Build conditions), this increase in delay would not be considered a significant impact based on the CEQR guidelines, since fewer than 90 passenger-car-equivalents (PCEs) were identified at this approach during the AM peak hour in the 2011 Build conditions.
PARKING
The proposed project would provide approximately 268 accessory spaces, which would accommodate the majority of the project’s residential parking demand. The remaining parking demand would be accommodated by the on-street parking available in the study area. Therefore, the proposed project would not significantly impact the supply of parking in the study area.
TRANSIT AND PEDESTRIANS
SUBWAYS
The area is served by multiple subway lines, including the F and G along Smith Street (with two entrances), and the M and R subway lines along 4th Avenue at Union Street. Therefore, it is not expected that any single subway element (e.g., entrances or stairs) would experience trips in excess of the CEQR Technical Manual guideline threshold of 200. Therefore, the proposed project is not expected to result in significant adverse impacts to subway conditions.
BUSES
The number of bus trips generated by proposed project would be significantly below the CEQR threshold; therefore, a detailed analysis of bus service conditions is not warranted and no significant adverse impacts would occur.
PEDESTRIANS
The proposed project is not expected to result in significant adverse impacts to pedestrian circulation in the area; on the contrary, it would provide multiple pedestrian entrances/exits to the residential buildings and to the proposed commercial and community facility spaces. It would improve sidewalks along the project streets, provide new public pedestrian connections to the
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Final EIS Notice of Completion 363-365 Bond Street, CEQR No.08DCP033K new public open space along the Gowanus Canal and open new means of local pedestrian circulation. Therefore, no detailed analyses of pedestrian conditions are warranted.
AIR QUALITY
Air quality analyses for an environmental impact statement (EIS) typically consider four potential sources of pollutants and areas of air quality impacts: 1) the potential for pollutants from mobile sources (such as cars and trucks) to impact the ambient environment; 2) the potential for pollutants from the proposed heating systems to impact the surrounding environment and nearby residential buildings; 3) the potential for future residents of a residential building to be impacted by emissions from nearby industrial or commercial uses; and 4) the potential for pollutants from garages to impact ambient air quality. With respect to mobile source analyses, the proposed project would not generate enough vehicular traffic to result in an air quality impact from mobile sources. To ensure that the development would not result in any significant air quality impacts from HVAC emissions, an (E) designation would be provided as part of the proposed zoning. The text of the (E) designation would be as follows:
Tax Block 452, Tax Lots 1, 15: Any new development must use natural gas as the type of fuel for HVAC systems. Boiler exhaust stack(s) for all development shall be located on the highest tier of each building. Tax Block 458, Lot 1: Any new development must use natural gas as the type of fuel for HVAC systems. Boiler exhaust stack(s) for all development shall be located on the highest tier of each building.
With these restrictions in place, no significant adverse air quality impacts would result from the proposed project’s HVAC systems.
With respect to local industrial sources, it was determined based on air permits for nearby industrial operations (e.g., concrete batching plants) and air quality modeling of these facilities that future project residents would not experience significant adverse air quality impacts from nearby industrial sources. The garage analysis found that neither future project residents nor the surrounding neighborhood would be impacted by the proposed on-site parking garages.
In addition, to these four analyses, an analysis was performed to determine if local odor conditions near the project site could impact the proposed project. Based on real-time sampling of odors at the project site, it was determined that during periods with weather conditions conducive to high concentrations of hydrogen sulfide (H2S)—an indicator of potential odors—near the Gowanus Canal, the hourly average concentration of H2S could exceed the nuisance-based standard for this pollutant, resulting in a significant adverse odor impact.
NOISE
The proposed project would not result in any significant adverse stationary or mobile source noise impacts. In addition, noise levels in the proposed project’s new publicly-accessible open space areas, principally from vehicular traffic on the adjacent streets, would not result in a significant noise impact.
CONSTRUCTION
Construction of the proposed project is expected to last approximately 24 months, beginning in April 2009 and ending in 2011.
Prior to construction, environmental remediation would be performed to address any hazardous materials currently existing on the site and demolition of the existing buildings.
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Final EIS Notice of Completion 363-365 Bond Street, CEQR No.08DCP033K Construction of the proposed project would involve several stages, some which would overlap: demolition of the existing buildings and environmental remediation; excavation/grading, foundation; building structure construction; and interior construction and finishing. Construction would generally proceed simultaneously on both blocks comprising the project site. Activities would begin with demolition of the existing buildings, and any required remediation of the site. Milling and crushing of any demolished materials approved for reuse, if any, would also be done during this stage of construction. Concurrently, the site would be graded, and the driving of piles for support of the building foundations and new sewer lines, as well as the driving of sheet piles for the restoration of the canal bulkhead would also be performed. Foundations work would then begin, followed by superstructure and building envelope activities focusing on the east side of the site to allow for an early start to construction of the canal esplanade. Mechanical, electrical, and interior finish work will follow the superstructure activities; a final site finish stage will complete construction activities prior to occupancy.
PROPOSED INFRASTRUCTURE IMPROVEMENTS
In addition to the building construction on site, there would also be improvements to the infrastructure. The proposed project would separate the stormwater flow from the sanitary flow by installing new separate stormwater sewers in 1st and 2nd Streets, with new stormwater outfalls to the Gowanus Canal. These new stormwater sewers would be designed and constructed in accordance with DEP standards and approval.
PROPOSED WATERFRONT OPEN SPACE AND BULKHEAD IMPROVEMENTS
The proposed project would modify the existing infrastructure by installing a new steel sheet pile bulkhead for the entire length of the waterfront. To minimize extending the marine infrastructure into the water, the proposed new sheeting would be installed either in place or against the face of the existing timber sheathing. An archaeological field investigation would occur either in advance of or in concert with the bulkhead reconstruction and storm water outfall installation (in coordination with LPC), and would serve as mitigation for the significant adverse impact to the bulkhead. An Archaeological Testing Protocol in compliance with the LPC Guidelines for Archaeological Work in New York City guidelines would be prepared and implemented in coordination with LPC. In addition, as requested by SHPO, an Unanticipated Discovery Plan for both human and non-human remains would be prepared in consultation with SHPO and implemented during project-related construction at the site.
TYPICAL CONSTRUCTION PRACTICES
The proposed project will employ typical construction practices that have proven successful and have been found to be necessary to complete projects of this magnitude in a confined urban area. All deliveries, material removals, and hoist uses have to be tightly scheduled to maintain an orderly work area and to keep the construction on schedule and within budget. The applicant would designate a contact person for community relations throughout the construction period. This person would serve as the contact for the community to voice concerns about construction activities, and would be available to meet with the community to resolve concerns or problems.
Typical construction practices include:
• Remedial Action Plan(RAP)/Construction Health and Safety Plan (CHASP). To minimize the potential for impacts to the community and construction workers, all demolition, excavation, and construction work involving soil disturbance would be performed in accordance with a RAP/CHASP approved by DEP.
• Construction Equipment. Typical equipment used for demolition, excavation, and foundation work would include excavators, bulldozers, portable crushing equipment,
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Final EIS Notice of Completion 363-365 Bond Street, CEQR No.08DCP033K
backhoes, compaction equipment, tractors, jackhammers, and concrete pumping trucks. Other equipment that would be used include pile drivers, dump trucks and loaders, concrete trucks, and back hoes. Trucks would deliver concrete and other building materials, and remove excavated material as well as demolition and construction debris. The construction equipment likely to be used during erection of the superstructure would include compressors, cranes, concrete pumps, hoists, bending jigs, and welding machines.
• Deliveries and Access. Access to the construction sites would be controlled. Work areas would be fenced off to provide security protection, and limited access points for workers and trucks would be provided. Security guards and flaggers would be posted, and all persons and trucks would have to pass through security points. After work hours, the gates would be closed and locked. Material deliveries to the site would be controlled and scheduled. Unscheduled or haphazard deliveries would be minimized.
• Hours of Work. Construction activities for the proposed buildings would take place in accordance with New York City laws and regulations, which allow construction activities to take place between 7:00 AM and 6:00 PM. Typically, work would end at 3:30 PM, but could be extended until 6:00 PM. Extended workday activities would not include all construction workers on site, but only those involved in the specific task. Extended workdays would occur during foundation and superstructure tasks, and limited extended workdays could occur during other tasks over the course of construction. It is possible that weekend work would be required; it would require a permit from the New York City Department of Buildings (DOB) and, in certain instances, approval of a noise mitigation plan from DEP under the City’s Noise Code.
• Sidewalk and Lane Closures. Depending on the location and stage of construction at a particular time on the project site, construction activities would require temporary sidewalk and lane closures along Bond Street, Carroll Street, 1st Street or 2nd Street. Sidewalk and lane closures require NYCDOT permitting and compliance with measures to safeguard the public.
• Staging and Laydown Areas. During the early stages of construction, the laydown and staging areas would be accommodated on the unconstructed parcels. During construction of the proposed buildings’ superstructure, laydown areas would likely be on the curb lane of Bond Street, Carroll Street, 1st Street or 2nd Street.
• Rodent Control. Construction contracts would include provisions for a rodent control program in coordination with appropriate public agencies.
In sum, construction may at times be disruptive to nearby residential buildings during the construction period. However, since the proposed project will conform to all appropriate local and state regulations, there would be no significant adverse impacts from construction of the proposed project.
PUBLIC HEALTH
As per CEQR guidelines, a screening-level assessment was conducted to determine whether a public health analysis is warranted. The assessment determined that the proposed project would not results in significant adverse impacts related to air quality, hazardous materials, groundwater, solid waste management practices that could attract vermin, and noise. In addition, based on the technical analyses presented in earlier chapters of this EIS, the proposed project would not result in an exceedance of accepted federal, State, or local standards. The proposed project is not proposing any other actions that would result in significant public health concerns. Therefore, no further public health analysis is warranted and the proposed project would not result in significant adverse public health impacts.
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Final EIS Notice of Completion 363-365 Bond Street, CEQR No.08DCP033K MITIGATION
The proposed project may result in significant adverse impacts in the areas of historic resources, air quality, and traffic. Possible mitigation for these impacts is discussed below.
HISTORIC RESOURCES
The proposed project includes the construction of a new steel sheet pile bulkhead along the eastern boundary of the project site. An anchoring system consisting of “deadmen” and steel tie rods would be installed, and would extend up to 40 feet landward of the bulkhead. The tie rods would run from the new sheeting to the deadmen approximately every eight feet for the length of the bulkhead. The installation of the tie rods would require that trenches between the bulkhead and the deadmen be excavated. The installation of the tie rods could require removal of portions of the existing cribwork sufficient to allow the steel tie rods to pass through the area. The proposed bulkhead rehabilitation design described above may require modification based on the requirements of DEC and/or ACOE.
Two new storm water outfalls would also be constructed through the existing bulkhead, one at the end of 1st Street and the other at the end of 2nd Street. The proposed bulkhead work and storm water outfall installation described above would adversely impact portions of the existing bulkhead at the project site.
To mitigate the significant adverse impact on the existing bulkhead under CEQR, an archaeological field investigation would be undertaken in coordination with the LPC that would document the extent and significant characteristics of the portion of the Gowanus Canal bulkhead on the project site. The goals of the investigation would be to determine the length and width of a single crib, document and/or sample fill contained within the timber cribwork, and to evaluate and document the bulkhead’s construction, including the joinery between adjacent cribs. This field investigation would occur either in advance of or in concert with the bulkhead reconstruction and storm water outfall installation. An Archaeological Testing Protocol in compliance with the LPC’s Guidelines for Archaeological Work in New York City (2002) would be prepared and implemented in coordination with LPC.
AIR QUALITY
An analysis was performed to determine if local odor conditions near the project site could impact the proposed project. Based on real-time sampling of odors at the project site, it was determined that at times, the concentration of hydrogen sulfide (H2S)—an indicator of potential odors—was above the 10 ppb nuisance-based threshold. In accordance with the CEQR Technical Manual, these levels would constitute a potential significant odor impact that could occur with respect to both future open space users and residents at the project site.
Given that local waterway and infrastructure is assumed to be the greatest contributor of H2S, to the ambient condition, this impact could potentially be reduced through the implementation of the City-proposed infrastructure projects for the area by 2013 (described above) which include:
• Rehabilitation of the Gowanus Canal Flushing Tunnel—This rehabilitation will increase the capacity for water intake from the East River to the canal from 154 mgd to 215 mgd. This would improve water quality and dissolved oxygen levels, enhance flow through and circulation, and reduce stagnation and organic matter concentrations in the canal waters which is one potential source of H2S.
• Reconstruction of the Gowanus Pump Station—This reconstruction would result in the expansion of the capacity of the Gowanus Pump Station through the installation of four new pumps and the redirection of sewage to a force main that currently runs along the
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Final EIS Notice of Completion 363-365 Bond Street, CEQR No.08DCP033K
inside of the Flushing Tunnel. Because the current force main is not operational, that flow is diverted to the Bond Street sewer, which could be another source of H2S through manholes and vents. Moreover, relieving the capacity of the Bond Street combined sewer reduced the potential for CSO discharges into the canal (the reconstruction of the Pump Station and replacement of the force main is projected to reduce the annual volume of CSO discharges to the canal by 34 percent) which in-turn reduces another potential source of H2S.
• Dredging—Dredging the upper 750 feet of the Gowanus Canal will eliminate exposed sediment mounds which has previously been identified as another potential source of H2S in the area.
As a result of the above-described proposed infrastructure improvements, it is possible that the identified odor impacts could potentially be reduced by 2013 (or upon completion of dredging). Since it is anticipated that these improvements would be implemented after the proposed project’s build year, the odor impacts would be considered unmitigated unavoidable adverse impacts until the completion of the improvements. To the extent that none of these measures are implemented or in the event that such measures are ineffective, H2S levels at the site could remain above 10ppb for an hourly average, thereby constituting an unmitigated unavoidable adverse impact of the proposed project.
TRAFFIC
Two of the intersections in the study area would experience significant adverse traffic impacts as a result of the proposed project. The sections below identify the mitigation needed at each location.
Proposed Mitigation Measures Measures proposed to mitigate the project-related traffic impacts would primarily involve retiming signal controls to increase green time for impacted movements and prohibition of curbside parking at one of the intersection approaches to provide an additional travel lane. The proposed mitigation measures are summarized in Table S-3 and are discussed below.
Table S-3Proposed Mitigation Measures
Intersections AM Peak Hour PM Peak Hour
3rd Avenue and Carroll Street
Prohibit parking on the south curb of eastbound Carroll Street approach for approximately 150 feet
to provide an additional moving lane of traffic.
Shift 3 seconds of green time from the northbound/southbound phase to the eastbound phase.
4th Avenue and Carroll Street
Shift 4 seconds of green time from the northbound/southbound phase to the eastbound
phase.
Shift 2 seconds of green time from the northbound/southbound phase to the eastbound phase.
3RD AVENUE AND CARROLL STREET
The impact at the eastbound approach of Carroll Street at 3rd Avenue during the weekday AM peak hour could be mitigated by prohibiting the curbside parking along the south side of the eastbound approach for approximately 150 feet during the AM peak hour. Currently, the curbside parking on the south side of Carroll Street is regulated by alternate side parking (street cleaning) regulations. With the proposed mitigation measure in place, no vehicular parking/standing would be allowed during the weekday AM peak hour (displacing approximately 7 parking spaces at the intersection approach) to provide an additional travel lane. The displaced parking spaces would
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Final EIS Notice of Completion 363-365 Bond Street, CEQR No.08DCP033K increase the on-street parking utilization in the study area to approximately 98 percent during the early morning hours.
The impact at the eastbound approach of Carroll Street at 3rd Avenue during the weekday PM peak hour could be mitigated by shifting 3 seconds of green time from the northbound/southbound phase to the eastbound phase.
4TH AVENUE AND CARROLL STREET
The impact at the eastbound approach of Carroll Street at 4th Avenue during the weekday AM peak hour could be mitigated by shifting 4 seconds of green time from the northbound/ southbound phase to the eastbound phase.
The impact at the eastbound approach of Carroll Street at 4th Avenue during the weekday PM peak hour could be mitigated by shifting 2 seconds of green time from the northbound/ southbound phase to the eastbound phase.
It should be noted that all of the mitigation measures discussed above are subject to review and approval by NYCDOT.
ALTERNATIVES
Alternatives to the proposed project that were analyzed include the No Action Alternative, which assumes the project site would remain in its current condition and no zoning actions are approved; the As-of-Right Alternative, which assumes the project site is developed as-of-right with uses under the current M2-1 zoning district; and a Lesser Density Alternative, which considers the development of the project site at 2.7 FAR with market rate housing and without the inclusion of any affordable housing.
NO ACTION ALTERNATIVE
The No Action Alternative provides a baseline against which impacts of the proposed action may be compared. Under the No Action Alternative it is assumed that no discretionary actions would be necessary and that there would not be any changes to the project site.
Similar to the proposed project, the No Action Alternative would not result in any significant adverse impacts on: land use, zoning, and public policy; socioeconomics; community facilities; open space; shadows; urban design and visual resources; neighborhood character; hazardous materials; infrastructure; solid waste; energy; transit and pedestrians; noise; and public health. Unlike the proposed project, the No Action Alternative would not result in significant adverse impacts on historic resources, air quality, or traffic.
The No Action alternative would not result in some of the beneficial aspects of the proposed project. For example, it would fail to implement waterfront redevelopment, open space, and inclusionary housing objectives for the Gowanus Canal. It would not extend by two blocks the residential character of the adjacent Carroll Gardens neighborhood, provide the community facility space proposed by the project, provide new public views of the Carroll Street Bridge and Operator’s House, redevelop and stabilize the timber crib bulkhead; improve the quality of local groundwater and surface waters, or remediate the site for contaminated materials.
AS-OF-RIGHT ALTERNATIVE
Under this alternative, it is assumed that the existing uses on the project sites would be replaced with an As-of-Right Alternative warehouse/storage use (two buildings) covering the site and totaling about 295,000 zoning square feet. It would be up to 60 feet high and provide on-site parking.
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Final EIS Notice of Completion 363-365 Bond Street, CEQR No.08DCP033K Similar to the proposed project, the As-of-Right Alternative would not result in any significant adverse impacts on: land use, zoning, and public policy; socioeconomics; community facilities; open space; shadows; historic resources; urban design and visual resources; neighborhood character; natural resources; hazardous materials; infrastructure; solid waste; energy; transit and pedestrians; noise; construction; and public health. The As-of-Right Alternative would generate approximately 43 and 13 more vehicle trips during the midday and PM peak hours than would the proposed project; however, it is anticipated that the mitigation measures proposed to address the impacts of the proposed project could similarly address any potential impacts of the As-of-Right Alternative. However, under the As-of-Right Alternative no such mitigation measures would be proposed since no CEQR review would be performed.
Under the As-of-Right Alternative, the project’s purpose and need and its objectives—including redevelopment of the waterfront with a new mix of housing and residential uses (including affordable housing) and open space—would not be achieved. Nor would the warehouse uses reinforce the existing patterns of residential development in the area or provide waterfront access for the community. It would not extend by two blocks the residential character of the adjacent Carroll Gardens neighborhood, provide the community facility space proposed by the project, open up new waterfront views of these historic resources, or improve the quality of local groundwater and surface waters. The construction health and safety plan required under the proposed project would not necessarily occur under this alternative.
LESSER DENSITY ALTERNATIVE
Under this alternative, it is assumed that the existing uses on the project site would be replaced with a market rate residential project that would provide approximately 320 housing units; no affordable housing would be provided. It is also assumed that a waterfront open space would be provided, as well as commercial and community facility uses similar to the proposed project.
Similar to the proposed project, the Lesser Density Alternative would not result in any significant adverse impacts on: land use, zoning, and public policy; socioeconomics; community facilities; open space; shadows; urban design and visual resources; neighborhood character; hazardous materials; natural resources; infrastructure; solid waste; energy; transit and pedestrians; noise; construction, and public health. With this alternative, there could be an adverse historic resources impact with respect to the historic Gowanus Canal bulkhead, but this alternative would also require a review by LPC under CEQR; therefore, mitigation would be required that would likely be similar to the proposed project. It is expected that the Lesser Density Alternative would result in significant adverse traffic impacts at the same locations as with the proposed project, and that mitigation measures similar to those recommended for the proposed project would be required to mitigate such impacts. Also, similar to the proposed project, the unmitigated, unavoidable adverse impact with respect to odors would occur under this alternative.
UNAVOIDABLE SIGNIFICANT ADVERSE IMPACTS
An analysis was performed to determine if local odor conditions near the project site could impact the proposed project. Based on real-time sampling of odors at the project site, it was determined that at times, the concentration of H2S—an indicator of potential odors—was above the 10 ppb nuisance-based threshold. In accordance with the CEQR Technical Manual, these levels would constitute a potential significant odor impact that could occur with respect to both future open space users and residents at the project site.
Given that local waterway and infrastructure is assumed to be the greatest contributor of H2S, to the ambient condition, this impact could potentially be reduced or eliminated through the implementation of the City-proposed infrastructure projects for the area by 2013 which include:
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Final EIS Notice of Completion 363-365 Bond Street, CEQR No.08DCP033K
• Rehabilitation of the Gowanus Canal Flushing Tunnel—This rehabilitation will increase the capacity for water intake from the East River to the canal from 154 mgd to 215 mgd. This would improve water quality and dissolved oxygen levels, enhance flow through, circulation and reduce stagnation and organic matter concentrations in the canal waters which is one potential source of H2S.
• Reconstruction of the Gowanus Pump Station—This reconstruction would result in the expansion of the capacity of the Gowanus Pump Station through the installation of four new pumps and the redirection of sewage to a force main that currently runs along the inside of the Flushing Tunnel. Because the current force main is not operational, that flow is diverted to the Bond Street sewer, which could be another source of H2S through manholes and vents. Moreover, relieving the capacity of the Bond Street combined sewer reduced the potential for CSO discharges into the canal (the reconstruction of the Pump Station and replacement of the force main is projected to reduce the annual volume of CSO discharges to the canal by 34 percent) which in-turn reduces another potential source of H2S.
• Dredging—Dredging the upper 750 feet of the Gowanus Canal will eliminate exposed sediment mounds which has previously been identified as another potential source of H2S in the area.
As a result of the above-described proposed infrastructure improvements, it is possible that the identified odor impacts could potentially be reduced or eliminated by 2013 (or upon completion of dredging). Since it is anticipated that these improvements would be implemented after the proposed project’s build year, the odor impacts would be considered unmitigated unavoidable adverse impacts until the completion of the improvements. To the extent that none of these measures are implemented or in the event that such measures are ineffective, H2S levels at the site could remain above 10ppb for an hourly average, thereby constituting an unmitigated unavoidable adverse impact of the proposed project.
IRREVERSIBLE AND IRRETRIEVABLE COMMITMENT OF RESOURCES
Under the proposed project, both natural and man-made resources would be expended in the construction and implementation of the proposed project. These resources include the building materials used during construction; energy in the form of gas and electricity consumed during construction; and the human effort (time and labor) required to develop, construct, and operate various elements of the proposed project. These are considered irretrievably committed because their reuse for some purpose other than the proposed project would be highly unlikely. Although the proposed project would result in a net overall increase in open spaces and a wider variety of land uses, the land use changes associated with the development of the proposed project may also be considered a resource loss.
These commitments of land resources and materials are weighed against the public purpose and benefits of the proposed development: to facilitate the development of underutilized parcels on a former waterfront industrial site along the Gowanus Canal with residential (including affordable housing), community facility and commercial uses, and to provide a publicly-accessible waterfront open space for the community.
GROWTH-INDUCING ASPECTS OF THE PROJECT
The goal of the proposed project and actions are to allow for the redevelopment of a former waterfront industrial site along the Gowanus Canal with residential and other uses including a publicly-accessible waterfront open space. While this development would support the City and State economies, it would not be expected to induce additional growth outside the project site.
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·Final EIS Notice.ofCompletion 363-365 Bond Street, CEQR No.08DCP033K
Much of the area surrounding the project site, including west of Bond Street and east of 4th A venue has been fully developed with residential development and commercial uses since the late 19th century (e.g., the Carroll Gardens and Park Slope neighborhoods). The intervening blocks between these long established residential neighborhoods along the Gowanus Canal have historically been developed with industrial uses and the level and type of development in this area is controlled by zoning which consists primarily of M2 and Ml zoning districts. The proposed project and related actions are specific to the two project blocks only. The remaining Gowanus area is also subject to the planning framework now being developed by the New York City Department of City Planning, which is a separate action examining future land use proposals for the area that would allow residential, commercial, the continuation of manufacturing, and open space uses along the canal. Also, given the increasing attraction of the area for new uses (including commercial, residential and hotel), there are a number of No Build projects that will add these new uses to the area through the year 2011.
The proposed project and actions would not significantly affect socioeconomic conditions in the study area. It would not add a residential population that would significantly increase the local population. In addition, given the trends that have been occurring in the area over the past two decades, the new residents would be similar in demographic composition to the current population and the added housing, in particular the affordable housing, would serve the current housing needs and demands in the area. With the proposed project, the added employment would be associated with the proposed residential and commercial uses, but would not significantly alter the local employment conditions. In addition, the proposed project can use existing infrastructure and proposes only infrastructure improvements that are site specific (e.g., new storm outfalls, bulkheads) and necessary'for site development.
For all the reasons cited above, it is concluded that the proposed actions would not result in any growth-inducing impacts. *
Robert Dobruskin, AICP, Director Environmental Assessment and Review Division New York City Department of City Planning
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I
New York State Department of Environmental Conservation Division of Environmental Remediation, Region 2 One Hunters Point Plaza 47-40 21st Street, Long Island City, NY 11101-5407 Phone: (718) 482-6453 Fax: (718) 482-6390 Website: www.dec.ny.gov E-Mail: [email protected] July 19, 2011 David S. Yudelson Sive, Paget & Riesel P.C. 460 Park Avenue New York, NY 10022 Re: Remedial Action Plan 400 Carroll Street, Brooklyn, NY NYSDEC Spill Number 0400876 Dear Mr. Yudelson:
The Department has reviewed the July 2011 Revised Remedial Action Plan pertaining to the above-
referenced site, submitted by P. W. Grosser Consulting, Inc. (PWGC) on behalf of Wooden Bridge, LLC.
The revised remedial plan proposes excavation and off-site disposal of petroleum contaminated soils
from three “hot spot” areas which were previously intended for soil stabilization, as a more appropriate
remedial alternative. PWGC is proposing that soils in these three areas be excavated to a depth of
approximately seven feet below grade, with collection of post-excavation end-point soil samples from the
excavation sidewalls. Since the project site is located on the Gowanus Canal, soil erosion and sediment
controls will be installed prior to excavation activities. A summary report with conclusions and
recommendations for further actions will be prepared and submitted to DEC.
The Department approves the remedial action plan with the following comment:
• Post-excavation end-point soil samples should also be collected from the bottoms of the
excavations for to characterize any residual soil contamination.
Please note that the Responsible Party and its contractors are solely responsible for the safe execution of
this work plan and in particular, are responsible for identifying subsurface utilities and safeguarding the
structural integrity of any excavations, buildings, utilities, and other structures both on- and off-site that
may be adversely affected by the work. The Responsible Party and its contractors must obtain any local,
Joe Martens Commissioner
Page2 state or federal permits or approvals that may be required to perform this work, and are responsible for
the implementation of all appropriate health and safety measures during the performance of this work.
Please notify the Department in writing at least five (5) business days prior to performing any fieldwork
at the site. Feel free to contact me if you have any questions or comments.
Sincerely,
Ainura Doronova Environmental Engineer Division of Environmental Remediation NYSDEC Region 2 cc: Jon Kolleeny - NYSDEC File
UNITED STATES ENVIRONMENTAL PROTECTION AGENCY
REGION II
290 BROADWAY
NEW YORK, NEW YORK 10007-1866
October 2012 EPA update regarding the Lightstone Group proposal:
EPA has been asked to clarify how EPA’s anticipated dredgingcleanup would be affected by the Lightstone Group developmentproposal.
EPA’s conceptual approach to a coordinated cleanup includes:
1. addressing continuing upland sources before dredging reachesthat location;
2. where possible, upgrading bulkheads before dredging toreduce the cost and time needed to install temporarysheetpiling; and
3. reducing impacts of CSO discharges.
EPA believes that the Lightstone proposal would satisfy each ofthose goals if implemented:
1. EPA’s 2010 Remedial Investigation (RI) identified a minorarea of deep subsurface contamination at 400 Carroll Street. Lightstone has agreed to enter into an EPA administrativeorder to address this through a new engineered bulkheadsealed at the appropriate depth to isolate the contaminationfrom entering the Canal. Lightstone has also agreed toconduct additional EPA-recommended sampling and to addressany other areas of contamination under NYSDEC and NYCOERoversight.
2. The bulkhead would be engineered to EPA’s dredging depthspecifications, eliminating the need for temporarysheetpiling.
3. Lightstone’s proposal includes separating combined storm andsanitary discharges at and around the parcels. Lightstonehas agreed to consult and coordinate with EPA to ensure thatthere is a net CSO reduction and that separated stormwateris properly treated.
EPA supports coordinated cleanups of contaminated sites along theCanal to return land to productive use. EPA’s primary role insuch cleanups is to ensure that continuing contamination sourcesare addressed. If any part of a proposed project mightnegatively impact EPA’s cleanup, EPA would make that informationavailable and take appropriate steps. EPA does not have a rolein determining land use nor does EPA take a position on theappropriateness of a given redevelopment proposal.
UNITED STATES ENVIRONMENTAL PROTECTION AGENCY
REGION II
290 BROADWAY
NEW YORK, NEW YORK 10007-1866
Regarding the Lightstone Group proposal at the formerToll Brothers property
EPA is periodically contacted by potential developers ofproperties near the Gowanus Canal having questions regardingEPA’s anticipated cleanup of the Canal, whether contamination ispresent on such properties and about the scope of Superfundliability.
Three parcels, 400 Carroll Street, 363 Bond Street and 365 BondStreet, commonly known as the former Toll Brothers property, werepreviously re-zoned as residential by New York City. An initialphase of sampling was done for Tolls Brothers’ proposed cleanupand redevelopment.
During EPA’s 2010 Remedial Investigation (RI), EPA installed aseries of groundwater monitoring wells at parcels along the canalwhere historic industrial activity could have resulted incontamination. EPA installed such wells at 400 Carroll Street and365 Bond Street, the former location of two fuel terminals. EPA’s wells identified an area of deep subsurface contaminationat 400 Carroll Street. At the time that EPA’s RI report wasreleased, EPA also recommended that additional sampling beconducted at the Toll Brothers parcels prior to redevelopment toensure a thorough cleanup.
In 2011, in consultation with EPA, the owners of 400 CarrollStreet did further sampling to delineate the area of concern toEPA. Sampling results to date indicate that although this area ofcontamination is small, localized, and at a depth (20+ feet belowthe water table) that would not impact future development of thesite, it could never the less impact the Canal sediment throughmigration.
The owners of 400 Carroll Street subsequently indicated to EPAthat they were prepared to address this minor hotspot through anew engineered bulkhead that is sealed at the appropriate depthand will isolate the contamination from entering the Canal andprevent Canal contamination from entering the property. Theowners also agreed to address under NYSDEC and NYCOER oversightthe remainder of the sites, including any other areas ofcontamination.
2
Recently the Lightstone Group indicated to EPA that they areprepared to conduct that work at 400 Carroll Street as well asany necessary additional sampling and cleanup work on the othertwo parcels under the oversight of EPA and NYSDEC. We haverecently reviewed and commented on a delineation work plan andwill continue to work with the Lightstone Group to properlydelineate and scope the remediation of any significantcontamination on the properties. The work would likely beconducted pursuant to an EPA administrative order which wouldprovide Superfund liability protection in addition to thatavailable under Superfund’s “Bone Fide Prospective Purchaser”provisions.
EPA supports the cleanup of contaminated sites along the Canalwhich would result in returning land to productive use. EPA’sprimary role in site cleanups along the Canal is to ensure thatcontinuing sources of contamination to the canal are addressed.
As with Lightstone’s proposal, it also beneficial to restore thedeteriorating bulkheads that permit contaminants to enter thecanal and separate the combined storm and sanitary dischargesfrom upland properties. EPA does not have a role in determiningland use for such properties nor does EPA take a position on theappropriateness of a given redevelopment proposal. State and cityagencies normally have the lead for determining the level ofcleanup necessary for a given land use project. EPA, however,routinely consults with those agencies when EPA identifies anypotential concerns.
Although EPA believes that cleanup work is necessary at theLightstone parcels and has been working cooperatively with theproject sponsor to accomplish this, EPA does not consider thesethree parcels to be significant sources compared to othercontaminated locations along the Canal. If implemented, this workwould control one of the smaller upland sources to the Canal andeliminate the time and expense of installing temporary sheetpiling to prevent bulkhead collapse along these parcels duringfuture remedial dredging.
September 2012
Remedial Investigation Work Plan Proposed 363 Bond Street Development
APPENDIX D
HEALTH AND SAFETY PLAN
(HASP)
HEALTH AND SAFETY PLAN
FOR
SITE INVESTIGATION WORK PLAN
363 Bond Street & 400 Carroll Street
Brooklyn, New York
Prepared For:
The Lightstone Group
460 Park Avenue, 13th Floor
New York, New York 10022
Prepared By:
Langan Engineering, Environmental, Surveying
and Landscape Architecture, D.P.C.
619 River Drive Center 1
Elmwood Park, New Jersey 07407 NJ Certificate of Authorization No: 24GA27996400
August 2012
Updated July 2013
100287501
ENVIRONMENTAL HEALTH AND SAFETY PLAN
Client: The Lightstone Group
Project: PHASE II REMEDIAL INVESTIGATION
Location: 363 Bond Street & 400 Carroll Street, Brooklyn, New York
Chemical Hazards: VOCs, SVOCs, Metals, PCBs
Prepared By: Langan Engineering, Environmental, Surveying and
Landscape Architecture, D.P.C.
Version: 1
Date: July 2013
Client Contact: Dennis Freed
Langan Project Manager (PM): Chris McMahon
Langan Health & Safety Coordinator (HSC): Tony Moffa, CHMM
Langan Site Supervisor Field Personnel
Langan Site Safety Officer (SSO): Field Personnel
LANGAN ENGINEERING AND ENVIRONMENTAL SERVICES, INC. (LANGAN) AND LANGAN
SUBCONTRACTORS DO NOT GUARANTEE THE HEALTH OR SAFETY OF ANY PERSON
ENTERING THIS SITE. DUE TO THE NATURE OF THIS SITE AND THE ACTIVITY OCCURRING
THEREON, IT IS NOT POSSIBLE TO DISCOVER, EVALUATE, AND PROVIDE PROTECTION FOR
ALL POSSIBLE HAZARDS WHICH MAY BE ENCOUNTERED. STRICT ADHERENCE TO THE
HEALTH AND SAFETY GUIDELINES SET FORTH HEREIN WILL REDUCE, BUT NOT ELIMINATE,
THE POTENTIAL FOR INJURY AT THIS SITE. THE HEALTH AND SAFETY GUIDELINES IN THIS
PLAN WERE PREPARED SPECIFICALLY FOR THIS SITE AND SHOULD NOT BE USED ON ANY
OTHER SITE WITHOUT PRIOR RESEARCH AND EVALUATION BY A TRAINED HEALTH AND
SAFETY SPECIALIST.
APPROVALS
By signature, the personnel identified below hereby acknowledge that they have reviewed this
Environmental Health and Safely Plan (EHS Plan) and agree to comply with the requirements
contained therein as well as the applicable provisions of 29 CFR Parts 1910 and 1926. The
undersigned also acknowledge and accept that this EHS Plan is the project EHS Plan for the
site work described in the Phase II Investigation Work Plan (Work Plan). Furthermore, in
reviewing and accepting this EHS Plan, as currently written, the undersigned agree that to the
best of their knowledge, this EHS Plan adequately identifies the activities and hazards
associated with work at this site and describes the appropriate and necessary precautions and
protections for site workers required by the applicable OSHA statutes and regulations.
7/10/2013
LANGAN Project Manager - PM (Chris McMahon) Date
7/10/2013____
LANGAN Health and Safety Coordinator (Tony Moffa, CHMM) Date
LANGAN Site Supervisor Date
LANGAN Site Safety Officer ‟ SSO Date
TOC - i
TABLE OF CONTENTS
1.0 INTRODUCTION ................................................................................................................. 1
1.1 Purpose and Policy ................................................................................................ 1
1.2 Site Descriptions .................................................................................................... 1
2.0 PROJECT TEAM ORGANIZATION AND RESPONSIBILITIES ........................................... 2
2.1 Project Manager ..................................................................................................... 2
2.2 Site Supervisor/Site Safety Officer (SSO) ............................................................ 3
2.3 Health and Safety Coordinator (HSC) ................................................................... 4
2.4 Work Team ............................................................................................................. 5
3.0 HAZARDS ANALYSIS ........................................................................................................ 5
3.1 Chemical Exposure Hazards .................................................................................. 5
3.2 Biological Hazards ................................................................................................. 6
3.2.1 Blood-Borne Pathogens ............................................................................ 6
3.2.2 Animals ...................................................................................................... 6
3.2.3 Insects ........................................................................................................ 7
3.2.4 Wound Care ............................................................................................... 7
3.3 Physical Hazards .................................................................................................... 7
3.3.1 Temperature Extremes ............................................................................... 7
3.3.2 Noise and Air Resources .......................................................................... 8
3.3.3 Hand and Power Tools ............................................................................. 8
3.3.4 Slips, Trips, and Falls ................................................................................ 9
3.3.5 Fire and Explosion .................................................................................... 9
3.3.6 Material Handling ..................................................................................... 9
3.3.7 Drill Rig Operations ................................................................................ 10
3.3.8 Electrical Safety ...................................................................................... 11
3.3.9 Utilities .................................................................................................... 11
3.3.10 Vehicular Traffic ...................................................................................... 11
3.4 Task Hazard Analysis ........................................................................................... 11
3.4.1 Soil Borings Installations ....................................................................... 11
4.0 Personal PROTECTIVE EQUIPMENT (PPE) ..................................................................... 12
4.1 Levels of Protection ............................................................................................. 12
4.2 Respirator Fit-Test ............................................................................................... 14
4.3 Respirator Cartridge Change-Out Schedule ....................................................... 14
5.0 MONITORING PROGRAM ............................................................................................... 14
5.1 Community Air Monitoring Plan ......................................................................... 15
5.1.1 Vapor Emission Response Plan ............................................................. 16
5.1.2 Major Vapor Emission ............................................................................ 17
5.1.3 Major Vapor Emission Response Plan ................................................... 17
5.2 Monitoring Equipment Calibration and Maintenance ....................................... 17
TABLE OF CONTENTS
(Continued)
TOC-ii
6.0 WORK ZONES and DECONTAMINATION ...................................................................... 18
6.1 Site Control .......................................................................................................... 18
6.2 Contamination Control ........................................................................................ 18
6.2.1 Personnel Decontamination Station ..................................................... 18
6.2.2 Minimization of Contact with Contaminants ....................................... 19
6.2.3 Personnel Decontamination Sequence ................................................. 19
6.2.4 Emergency Decontamination ................................................................. 19
6.2.5 Hand-Held Equipment Decontamination .............................................. 20
6.3 Communications .................................................................................................. 20
7.0 MEDICAL SURVEILLANCE .............................................................................................. 21
8.0 Medical Surveillance Program Requirements ............................................................... 21
9.0 EMERGENCY RESPONSE PLAN ..................................................................................... 21
9.1 Responsibilities .................................................................................................... 21
9.1.1 Health and Safety Coordinator (HSC) .................................................... 21
9.1.2 Site Safety Officer (SSO) ........................................................................ 22
9.1.3 Emergency Coordinator ......................................................................... 22
9.1.4 Site Personnel ......................................................................................... 22
9.2 Communications .................................................................................................. 23
9.3 Local Emergency Support Units ......................................................................... 23
9.4 Pre-Emergency Planning ..................................................................................... 23
9.5 Emergency Medical Treatment ........................................................................... 24
(directions from site to hospital found on Figure 2) .......................................... 24
9.6 Emergency Site Evacuation Routes and Procedures ......................................... 25
9.7 Fire Prevention and Protection ........................................................................... 25
9.7.1 Fire Prevention ........................................................................................ 25
9.8 Significant Vapor Release ................................................................................... 26
9.9 Overt Chemical Exposure .................................................................................... 26
9.10 Decontamination During Medical Emergencies ................................................ 26
9.11 Incident Reporting ............................................................................................... 27
9.12 Adverse Weather Conditions .............................................................................. 27
9.13 Spill Control and Response ................................................................................. 28
9.14 Emergency Equipment ........................................................................................ 30
9.15 Restoration and Salvage ..................................................................................... 30
10.0 TRAINING ......................................................................................................................... 30
10.1 General Health and Safety Training ................................................................... 30
10.2 Annual Eight-Hour Refresher Training ............................................................... 30
10.3 Site-Specific Training........................................................................................... 31
10.4 Onsite Safety Briefings ........................................................................................ 31
10.5 First Aid and CPR ................................................................................................. 31
10.6 Hazard Communication ....................................................................................... 32
TABLE OF CONTENTS
(Continued)
TOC-iii
11.0 RECORDKEEPING ............................................................................................................ 32
11.1 Field Change Authorization Request .................................................................. 32
11.2 Medical and Training Records ............................................................................. 32
11.3 Onsite Log ............................................................................................................ 32
11.4 Daily Safety Meetings (“Tailgate Talks”) ........................................................... 32
11.5 Exposure Records ................................................................................................ 33
11.6 Incident Reports ................................................................................................... 33
11.7 OSHA Form 300.................................................................................................... 33
11.8 Hazard Communication Program/MSDS ........................................................... 33
11.9 Work Permits ....................................................................................................... 33
12.0 FIELD PERSONNEL REVIEW ........................................................................................... 34
TABLE OF CONTENTS
(Continued)
TOC-iv
TABLES
Table 1 List of Known or Suspected Contaminants
Table 2 Chemical Exposure Limits
Table 3 Hazard Analysis
Table 4 Instrumentation Action Levels
Table 5 Personnel Protection Equipment Summary
FIGURES
Figure 1 Site Location Map
Figure 2 Emergency Hospital Route Map
ATTACHMENTS
Attachment A Material Safety Data Sheets (MSDSs)
Attachment B Field Change Authorization Request Form
Attachment C Accident/Incident Report Form
Attachment D Emergency Notification List
NJ Certificate of Authorization No. 24GA27996400
\\Langan.Com\Data\EP\Data5\100287501\Engineering Data\Environmental\Reports\2013-07 - OER Phase II RIWP REVISED (363 Bond-400 Carroll)\Appendix D - HASP\HASP_363 Bond
Street & 400 Carroll Street (2013-07-10).Doc
1
1.0 INTRODUCTION
1.1 Purpose and Policy
This Health and Safety Plan (HASP) has been developed to comply with the
regulations under Occupational Safety and Health Administration (OSHA)
29 CFR 1910.120(b)(4), Hazardous Waste Operations and Emergency
Response. The plan addresses activities associated with the Phase II Remedial
Investigation work to be conducted at 363 Bond Street & 400 Carroll Street,
Brooklyn, New York (see Figure 1). This EHS Plan establishes personnel
protection standards and mandatory safety practices and procedures.
Additionally, it assigns responsibilities, establishes standard operating
procedures, and provides for contingencies that may arise while operations are
being conducted at known or suspected hazardous waste sites.
The provisions of this HASP are mandatory for all on-site personnel. Although
for use only by Langan personnel, HASPs prepared by subcontractors must
conform to the requirements of this HASP at a minimum. All personnel who
engage in project activities must be familiar with this HASP, comply with its
requirements, and sign the Field Personnel Review Form (Section 12.0)
1.2 Site Descriptions
Please refer to the Remedial Investigation Workplan for the full job description
and scope of work. The following provides a general job description summary.
The subject site consists of two parcels identified as 363 Bond Street and
400 Carroll Street, located in Brooklyn, New York. The 363 Bond Street parcel
contains one and two-story light industrial buildings. The 400 Carroll Street parcel
is currently partially occupied; however, foundations of former fuel-oil
aboveground storage tanks (ASTs) remain.
Specifically, the proposed scope of work is designed to:
Identify the potential presence and extent of impacted soil vapor, soil,
and/or groundwater at the site;
Delineate contaminant(s) of concern that were identified in previous
environmental investigations; and,
2
Evaluate remediation options for any impacted soil vapor, soil, and/or
groundwater in accordance with NYSDEC and NYCOER regulations, if
required.
The scope of work for the proposed Subsurface Investigation includes the
following field tasks:
„ Project mobilization;
„ Completion of sub-slab soil vapor testing;
„ Completion of test borings and soil sampling; and,
„ Installation of groundwater monitoring wells and groundwater
sampling.
Following the drilling contractor obtaining the necessary permits, they will
mobilize the drill rig. Langan will oversee the completion of 12 soil borings to a
depth of up to 15-feet and subsequent monitoring well installation at 4 of these
locations. Additionally, Langan will oversee the completion of 10 sub-slab vapor
points and 15 deep soil vapor points.
2.0 PROJECT TEAM ORGANIZATION AND RESPONSIBILITIES
This section specifies the Langan Project Organization.
2.1 Project Manager
Assumes total control over site activities. Reports to upper-level management.
Has authority to direct response operations.
Responsibilities:
Prepares and organizes the background review of the situation, the Phase II
Environmental Investigation Work Plan (Work Plan), the site HASP, and the
field team.
Obtains permission for site access and coordinates activities with
appropriate officials.
Ensures that the Work Plan is executed and on schedule.
Briefs the field team on their specific assignments.
3
Coordinates with the Site Safety Officer (SSO) to ensure that health and
safety requirements are met.
Prepares the final report and support files on the response activities.
Serves as the liaison with public officials.
2.2 Site Supervisor/Site Safety Officer (SSO)
Advises the Project Manager on all aspects of health and safety on site. Stops
work if any operation threatens worker or public health or safety. Is directly
responsible for the field team and the safety of site operations.
Responsibilities:
Manages field operations.
Executes the Work Plan and schedule.
Enforces safety procedures.
Coordinates with the SSO in determining protection level.
Enforces site control.
Documents field activities and sample collection.
Serves as a liaison with public officials.
Ensures that all necessary Health and Safety equipment is available on site
and is functional.
Periodically inspects protective clothing and equipment.
Conducts all on-site air monitoring activities and modifies PPE requirements
based on action levels shown in Table 4.
Ensures that protective clothing and equipment are properly stored and
maintained.
Controls entry and exit at the Access Control points.
Coordinates health and safety program activities with the HSC.
Confirms each team member's suitability for work based on a physician's
recommendation.
Monitors the work parties for signs of stress, such as cold exposure, heat
stress, and fatigue.
Implements all elements of this EHS Plan.
4
Conducts periodic inspections to determine if this EHS Plan is being
followed.
Enforces the "buddy" system.
Knows emergency procedures, evacuation routes, and the telephone
numbers of the ambulance, local hospital, poison control center, fire
department, and police department.
Notifies, when necessary, local public emergency officials.
Coordinates emergency medical care.
Sets up decontamination lines and the decontamination solutions
appropriate for the type of chemical contamination on the site.
Controls the decontamination of all equipment, personnel, and samples from
the contaminated areas.
Assures proper disposal of contaminated clothing and materials.
Ensures that all required equipment is available.
Advises medical personnel of potential exposures and consequences.
Notifies emergency response personnel by telephone or radio in the event
of an emergency.
Assist in the preparation of all Root Cause Investigation Reports/
Preventative Action Plans for any incidents and or Close Calls.
2.3 Health and Safety Coordinator (HSC)
Responsibilities:
Assists SSO with development of the HASP, updating HASP as dictated by
changing conditions, jobsite inspection results, etc.
Assists SSO in conducting Jobsite Safety Inspections and assists with the
correction of shortcomings found.
Coordinates the activities of the Contract Medical Advisor staff in their EHS
Plan responsibilities.
Ensures training requirements are satisfied in a timely manner.
Ensures medical evaluations of Langan personnel are current.
5
Maintains all records on personnel (medical evaluation results, training and
certifications, accident investigation results, etc.).
Prepare any Root Cause Investigation Reports/Preventative Action Plans for
any incidents and or Close Calls.
2.4 Work Team
Vacuum truck operators, drillers, samplers, surveyors, etc. The work party must
consist of at least two people.
Responsibilities:
Safely completes the on-site tasks required to fulfill the Work Plan.
Complies with this HASP.
Notifies SSO of suspected unsafe conditions.
Report any unsafe or potentially hazardous conditions to the SSO.
Maintain knowledge of the information, instructions and emergency
response actions contained in this HASP.
Comply with roles, regulations and procedures as set forth in this HASP and
any revisions.
Prevent admittance to work sites by unauthorized personnel.
Inspect all tools and equipment, including PPE, daily prior to use.
3.0 HAZARDS ANALYSIS
This section presents all assessment of the chemical, biological, and physical hazards
that may be encountered during the tasks specified under this HASP (Section 3). A
detailed list of types of potential contaminants of concerns Langan anticipates to
encounter at different locations during the intrusive investigation is listed in Table 1 of
this HASP.
3.1 Chemical Exposure Hazards
Potential contaminants that may be encountered while conducting site
investigation activities include VOCs, SVOCs, metals, and PCBs and historic fill.
Some relevant properties of these contaminants are shown in Table 1.
6
On-site personnel will make efforts to avoid activities that could generate
potentially contaminated dust, and work upwind of potentially contaminated soils
and ground water during investigation activities. In addition to the site’s
suspected contaminants, materials used in the site investigation process itself
may potentially be hazardous to human health if they are not used properly.
Material Safety Data Sheets for materials that will be brought or used on site and
the known or suspected site contaminants are included in Attachment A.
3.2 Biological Hazards
During the course of the project, there is a potential for workers to come into
contact with biological hazards such as animals, insects, and blood-borne
pathogens.
3.2.1 Blood-Borne Pathogens
During the course of the project, there is a potential for workers to come
into contact with biological hazards such as animals and insects. As the
potential for exposure to blood borne pathogens during the investigation
is anticipated to be low, a Blood-borne Pathogen Exposure Plan (BBPEP)
is not required. A BBPEP will be prepared if site operation requires its
implementation. Regardless, a first aid kit will be available on site at all
times during work
3.2.2 Animals
During site operations, animals such as dogs, cats, pigeons, mice, and
rats may be encountered. Workers shall use discretion and avoid all
contact with animals. Bites and scratches from dogs and cats can be
painful and if the animal is rabid, the potential for contracting rabies
exists. Contact with rat and mice droppings may lead to contracting
hantavirus. Inhalation of dried pigeon droppings may lead to psittacosis.
Cryptococcosis and histoplasmosis are also diseases associated with
exposure to dried bird droppings but these are less likely to occur in this
occupational setting.
7
3.2.3 Insects
Insects, including bees, wasps, hornets, mosquitoes, spiders, and ticks
may be present at the site. Some individuals may have a severe allergic
reaction to an insect bite or sting that can result in a life threatening
condition. In addition, mosquito bites may lead to St. Louis encephalitis
or West Nile encephalitis.
3.2.4 Wound Care
A source of occupational exposure may occur when an employee gives
First Aid and or CPR to an individual who had infectious blood. The
occupational exposure occurs when there is the possibility for an
employee’s eyes, mucous membranes, non-intact skin (i.e., cut and
abraded skin) to come into contact with potentially infectious materials
from another employee. If an accident were to occur where First Aid
would need to be administered, the person administering the First Aid
will presume that any wounds and materials used are contaminated with
BBP and should wear the appropriate PPE to prevent contact with these
materials. Additionally, should the use of First Aid materials and or
clothing that was potentially contaminated with BBP be encountered
these materials should be property containerized and transported to the
nearest hospital for proper disposal.
3.3 Physical Hazards
3.3.1 Temperature Extremes
Hot Temperatures
Heat stress is a significant potential hazard, which is greatly exacerbated
with the use of PPE, in hot environments. The potential hazards of
working in hot environments include dehydration, cramps, heat rash, heat
exhaustion, and heat stroke. If onsite workers exhibit the signs of heat
exhaustion or heat stroke, they should seek immediate medical attention.
Cold Temperatures
Workers may be exposed to the hazard of working in a cold environment.
Potential hazards in cold environments include frostbite, trench foot or
8
immersion foot, hypothermia, as well as slippery surfaces, brittle
equipment, poor judgment, and unauthorized procedural changes. In
order to prevent frostbite, hypothermia, trench foot and immersion foot,
the workers are responsible for dressing warmly in layers with thick
socks, gloves, and appropriate head and face gear. Upon the onset of
discomfort due to the cold, onsite workers should take regular five to ten
minute breaks to warm up inside nearby buildings and to drink warm
fluids. Please note that the NYCDEP statute prohibits idling an engine for
more than three minutes (one-minute if adjacent to a school). This statue
includes the use of a vehicle for the purpose of warming up employees.
As such, all contractors and employees shall identify a place to warm up
in advance. If discomfort continues and the onsite workers start to
exhibit the signs of frostbite, hypothermia, trench foot or immersion foot,
they should seek immediate medical attention.
3.3.2 Noise and Air Resources
Noise is a potential hazard associated with the operation of heavy
equipment, power tools, pumps and generators. Hearing protection is
required for noise levels of greater than 85 dBA.
The New York City Department of Environmental Protection (NYCDEP)
has initiated construction noise rules effective 1 July 2007. Contractors
employing construction equipment such as vacuum excavators, drill rigs,
and jackhammers, are required by the rules to have notarized
Construction Noise Mitigation Plans. Noise mitigation measures may
include mufflers, etc. Boring activities will occur during daytime hours
only to minimize noise disturbance to the community. In addition, no
vehicles will idle for more than three minutes (one-minute adjacent to a
school) when not in use for powering a tool.
3.3.3 Hand and Power Tools
In order to complete the various tasks for the project, personnel will
utilize hand and power tools. The use of hand and power tools can
present a variety of hazards, including physical harm from being struck by
flying objects, being cut or struck by the tool, fire, and electrocution.
Proper personal protective equipment shall be worn while utilizing hand
9
and power tools. Ground Fault Circuit Interrupters (GFCIs) are required
for all portable electric tools.
3.3.4 Slips, Trips, and Falls
Working in and around the site will pose slip, trip and fall hazards due to
equipment, piping, slippery surfaces that may be oil covered, or from
surfaces that are wet from rain or ice. Potential adverse health effects
include falling to the ground and becoming injured or twisting an ankle.
Good housekeeping at the site must be maintained at all times.
3.3.5 Fire and Explosion
Prior to starting all excavation and boring work, a review of appropriate
New York City maps will be conducted to identify potential hazards. The
possibility of encountering fire and explosion hazards exists from under-
ground utilities and gases; therefore, all excavation/boring equipment
must be grounded.
3.3.6 Material Handling
Manual lifting of heavy objects may be required. Failure to follow proper
lifting techniques can result in back injuries and strains. Back injuries are
a serious concern as they are the most common workplace injury, often
resulting in lost or restricted work time, and long treatment and recovery
periods.
Whenever possible, heavy objects must be lifted and moved by
mechanical devices rather than by manual effort. The mechanical
devices will be appropriate for the lifting or moving task and will be
operated only by trained and authorized personnel. Objects that require
special handling or rigging will only be moved under the guidance of a
person who has been specifically trained to move such objects, such as a
Master Rigger or equivalent. Lifting devices, including equipment, slings,
ropes, chains, and straps, will be inspected, certified, and labeled to
confirm their weight capacities. Defective equipment will be taken out of
service immediately and repaired or destroyed.
10
The wheels of any trucks being loaded or unloaded, and/or parked on an
incline, will be chocked to prevent movement. If applicable, outriggers
will be extended on a flat, firm surface during operation. The lift and
swing path of a crane/equipment will be watched and maintained clear of
obstructions. Personnel will not pass under a raised load, nor will a
suspended load be left unattended. Personnel will not be carried on
lifting equipment, unless it is specifically designed to carry passengers.
All reciprocating, rotating, or other moving parts will be guarded at all
times. Accessible fire extinguishers will be made available in all
mechanical lifting devices. All material must be stored in tiers, racked,
blocked, or otherwise secure to prevent sliding, falling, or collapse. All
loads/material will be verified to be secure before transportation.
3.3.7 Drill Rig Operations
In order to complete soil borings, a direct-push drill rig with hollow stem
auger capability will be used. Working with and near this equipment
poses many potential hazards, including being struck by or against, or
pinched/caught by moving parts. These hazards can result in serious
physical harm. Other hazards include electrocution and explosion due to
encountering overhead or underground utilities.
Drill rigs for hollow stem auger drilling and other machinery with exposed
moving parts must be equipped with an operational emergency stop
device. Drillers and other field personnel must be aware of the location
of this device. This device must be tested prior to job initiation and
periodically thereafter. The driller and helper shall not simultaneously
handle augers unless there is a standby person to activate the
emergency switch. Only equipment that has been approved by the
manufacturer may be used in conjunction with site equipment and
specifically to attach sections of drilling tools together. Pins that protrude
excessively from augers shall not be allowed.
The driller must never leave the controls while the tools are rotating
unless all personnel are kept clear of rotating equipment. A remote
sampling device must be used to sample drill cuttings if the tools are
rotating or if the tools are readily capable of rotating. Samplers must not
11
reach into or near the rotating equipment. Drillers, helpers, and other
field personnel must secure all loose clothing when in the vicinity of
drilling operations. No person shall climb the drill mast while tools are
rotating or without the use of ANSI-approved fall protection (approved
belts, lanyards and a fall protection slide rail) or portable ladder that
meets the requirement of the OSHA standard.
3.3.8 Electrical Safety
Although not anticipated, personnel may utilize hand and power tools.
The use of hand and power tools can present a variety of hazards,
including physical harm from being struck by flying objects, being cut or
struck by the tool, fire, and electrocution. Ground Fault Circuit
Interrupters (GFCIs) are required for all portable electric tools.
Construction vehicles and equipment will have grounds mounted to
them.
3.3.9 Utilities
Prior to the start of any intrusive work, the location of above-ground and
underground utilities and other structures will be completed by the
contractor/subcontractor responsible for completing construction activities.
3.3.10 Vehicular Traffic
Portions of site activities (load in and load out) will be conducted in the
street so vehicular and pedestrian traffic will be present. Appropriate
precautions to protect to works and civilians should be used including the
use of cones and traffic vests as appropriate.
3.4 Task Hazard Analysis
3.4.1 Soil Borings Installations
Special attention shall be given to establishing the location of any
underground utilities prior to boring or drilling. Prior to beginning the site
investigation work, the N.Y. One Call Center will be contacted by the
boring/drilling contractor for utility mark-outs. Pressure safety valves and
hose whip prevention devices will be installed and operational on any air
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compressors, hoses, and their tools to be used on site. Additionally, all
appropriate and current FDNY Certificates of Fitness (C of F) cards must
be on site for those workers using equipment where C of Fs are
required.
Chemical exposure may also occur as excavation cuttings are handled,
and samples are collected. Activities will be conducted in Level D, but
personnel should be prepared to upgrade to Level C, as appropriate,
based on field screening criteria.
If evidence of historic contamination is encountered during test borings
other than what is part of the intended investigation, installation or
drilling, work will be stopped and emergency contacts listed in
Attachment D of this HASP will be immediately notified.
4.0 PERSONAL PROTECTIVE EQUIPMENT (PPE)
4.1 Levels of Protection
PPE must protect workers from the specific hazards they are likely to encounter
on site. Selection of the appropriate PPE must take into consideration:
(1) identification of the hazards or suspected hazards; (2) potential exposure
routes; and, (3) the performance of the PPE construction (materials and seams)
in providing a barrier to these hazards. Based on anticipated site conditions and
the proposed work activities to be performed at the site, Level D Protection will
be used. The upgrading/downgrading of these levels of protection will be based
on continuous air monitoring results as described in Section 5.0. The decision to
modify standard PPE will be made by the SSO after conferring with the Project
Manager. The levels of protection are described below.
Level D Protection
a. Safety glasses w/ sideshields or chemical splash goggles
b. Safety boots/shoes (toe-protected)
c. Hard hat
d. Long sleeve work shirt and work pants
e. Nitrile gloves
f. Hearing protection (as needed)
g. Reflective traffic vest
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Level D Protection (Modified)
a. Safety glasses w/ sideshields or chemical splash goggles
b. Safety boots/shoes (toe-protected)
c. Disposable chemical-resistant boot covers
d. Coveralls (polycoated Tyvek or equivalent to be worn when contact with
wet contaminated soil, groundwater, or non-aqueous phase liquids is
anticipated)
e. Hard hat
f. Long sleeve work shirt and work pants
g. Nitrile gloves
h. Hearing protection (as needed)
i. Reflective traffic vest
Level C Protection
a. Full face-piece, air-purifying, cartridge*-equipped, NIOSH-approved
respirator [*combo cartridge P100/OV/CL/HC/SD/CD/HS (escape)]
b. Inner (latex) and outer (nitrile) chemical-resistant glove
c. Chemical-resistant safety boots/shoes (toe-protected)
d. Disposable chemical-resistant boot covers
e. Hard hat
f. Long sleeve work shirt and work pants
g. Coveralls (Tyvek or equivalent, poly-coated Tyvek will be worn when
contact, or anticipated contact with wet contaminated soils, ground
water, and/or non-aqueous phase liquids (NAPL) is anticipated )
h. Hearing protection (as needed)
i. Reflective traffic vest
The action levels used in determining the necessary levels of respiratory
protection and upgrading to Level C, Level B, or Level A are summarized
in Table 2. The written Respiratory Protection Program is maintained by
the HSC in Langan’s Doylestown, Pennsylvania office. The monitoring
procedures and equipment are outlined in Section 5.0. Prior to the start
of any intrusive work, the location of above-ground and underground
utilities and other structures will be completed by the contractor/
subcontractor responsible for completing construction activities.
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4.2 Respirator Fit-Test
All Langan employees and subcontractors performing site work who could be
exposed to hazardous substances at the work site are required to be in
possession of a full face-piece, air-purifying respirator and have been
successfully quantitative fit-tested within the past year. Quantitative fit-test
records are maintained by the HSC.
4.3 Respirator Cartridge Change-Out Schedule
Respiratory protection is required to be worn when certain action levels (Table 2)
are reached. A respirator cartridge change-out schedule has been developed in
order to comply with 29 CFR 1910.134. The respirator cartridge change-out
schedule for this project is as follows:
Cartridges shall be removed and disposed of at the end of each shift, when
cartridges become wet or wearer experiences breakthrough, whichever
occurs first.
If the humidity exceeds 85%, then cartridges shall be removed and
disposed of after 4 hours of use.
Respirators shall not be stored at the end of the shift with contaminated
cartridges left on. Cartridges shall not be worn on the second day, no matter
how short the time period was the previous day they were used.
5.0 MONITORING PROGRAM
The following sections contain information describing the types, frequency and location
of real-time, integrated, and other monitoring.
Air monitoring results are partially used to provide data to determine when exclusion
zones (EZs) need to be established and when certain levels of PPE are required. For all
instruments, there are specific action level criteria which are used in making field health
and safety determinations. Other data, such as the visible presence of contamination or
the steady state nature of air contaminant concentrations, are also used in making field
health and safety decisions. Therefore, the SSO or Site Supervisor may establish an EZ
or require a person to wear a respirator even though atmospheric air contaminant
concentrations are below established HASP action levels.
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5.1 Community Air Monitoring Plan
Community air monitoring will be conducted in compliance with the Community
Air Monitoring Plan (CAMP) outlined below.
Monitoring for total organic vapors (TOVs) and particulate will be conducted
during all ground intrusive activities. Upwind concentrations will be measured at
the start of each workday to establish background concentrations. TOVs and
particulates will be monitored within the work zone and at the downwind
perimeter of the Site with a PID equipped with a 10.6 eV lamp and a DusTrak or
DataRAM, respectively. Monitoring equipment will be capable of calculating 15-
minute running average concentrations.
The following actions will be taken based on TOV levels measured:
If total organic vapor levels exceed 5 ppm above background for the 15-
minute average at the perimeter, work activities will be temporarily halted
and monitoring continued. If levels readily decrease (per instantaneous
readings) below 5 ppm above background, work activities will resume
with continued monitoring.
If total organic vapor levels at the downwind perimeter of the Site persist
at levels in excess of 5 ppm above background but less than 25 ppm,
work activities will be halted, the source of vapors identified, corrective
actions taken to abate emissions, and monitoring continued. After these
steps work activities will resume provided that the total organic vapor at
the perimeter of the Site is below 5 ppm above background for the 15-
minute average.
If the total organic vapor level is above 25 ppm at the perimeter of the
Site, activities will be shutdown.
The following actions will be taken based on particulate concentrations
measured:
If the downwind particulate level is 100 micrograms per cubic meter
(ug/m3) greater than background (upwind perimeter) for the 15-minute
period or if airborne dust is observed leaving the work area, then dust
suppression techniques will be employed. Work will continue with dust
suppression techniques provided that downwind particulate levels do not
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exceed 150 ug/m3 above the upwind level and provided that no visible
dust is migrating from the work area.
If, after implementation of dust suppression techniques, downwind
particulate levels are greater than 150 ug/m3 above the background level,
work will be stopped and a re-evaluation of activities initiated. Work will
resume provided that dust suppression measures and other controls are
successful in reducing the downwind particulate concentration to within
150 ug/m3 of the upwind level and in preventing visible dust migration.
In order to minimize the generation of dust, water will be sprayed on
soils to be excavated, as needed. Water will also be sprayed on any
areas of the Site where dust could be generated. A suitable dust control
material, such as calcium chloride, will be used, as necessary, in high-
traffic areas in order to minimize dust caused by vehicular traffic.
Action levels are also provided in Table 4.
5.1.1 Vapor Emission Response Plan
If the ambient air concentration of organic vapors exceeds 5 ppm above
background at the perimeter of the Site, intrusive activities will be halted
or vapor suppression controls will be employed, and monitoring
continued. When work shut-down occurs, downwind air monitoring as
directed by the Field Safety Officer will be implemented to ensure that
vapor emission does not impact the nearest residential or commercial
structure at levels exceeding those specified in the Major Vapor Emission
section.
If the organic vapor level decreases below 5 ppm above background,
intrusive activity can resume, provided:
o The organic vapor level at the downwind perimeter of the Site is
below 1 ppm over background, and
o More frequent intervals of monitoring, as directed by the Site
Health and Safety Officer, are conducted.
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5.1.2 Major Vapor Emission
If any organic levels greater than 5 ppm over background are identified at
the downwind perimeter of the Site, all work activities must be halted or
odor controls must be implemented.
If, following the cessation of the work activities, or as the result of an
emergency, organic levels persist above 5 ppm above background at the
downwind perimeter of the Site, then the air quality must be monitored
within 20 feet of the perimeter of the nearest residential or commercial
structure (20 Foot Zone).
If either of the following criteria is exceeded in the 20 Foot Zone, then
the Major Vapor Emission Response Plan shall automatically be
implemented.
o Sustained organic vapor levels approaching 5 ppm above
background for a period of more than 30 minutes, or
o Organic vapor levels greater than 5 ppm above background for
any time period.
5.1.3 Major Vapor Emission Response Plan
Upon activation, the following activities will be undertaken:
1. The local police authorities will immediately be contacted by
the Site Health and Safety Officer and advised of the situation;
2. Frequent air monitoring will be conducted at 30-minute
intervals within the 20 Foot Zone. If two successive readings
below action levels are measured, air monitoring may be
halted or modified by the Site Health and Safety Officer; and
All Emergency contacts will go into effect as appropriate.
5.2 Monitoring Equipment Calibration and Maintenance
Instrument calibration shall be documented and included in a dedicated safety
and health logbook or on separate calibration pages of the field book. All
instruments shall be calibrated before each shift. Calibration checks may be used
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during the day to confirm instrument accuracy. Duplicate readings may be taken
to confirm individual instrument response.
All instruments shall be operated in accordance with the manufacturers’
specifications. Manufacturers' literature, including an operations manual for each
piece of monitoring equipment will be maintained on site by the SSO/Site
Supervisor for reference.
6.0 WORK ZONES AND DECONTAMINATION
6.1 Site Control
Work zones are intended to control the potential spread of contamination
throughout the site and to assure that only authorized individuals are permitted
into potentially hazardous areas.
Any person working in an area where the potential for exposure to site
contaminants exists will only be allowed access after providing the SSO with
proper training and medical documentation.
Exclusion Zone (EZ) - All activities which may involve exposure to site
contaminants, hazardous materials and/or conditions should be considered an
EZ. Decontamination of field equipment will also be conducted in the
Contaminant Reduction Zone (CRZ) which will be located on the perimeter of the
EZ. The EZ and the CRZ will be clearly delineated by cones, tapes or other
means. The SSO/Site Supervisor may establish more than one EZ where
different levels of protection may be employed or different hazards exist. The
size of the EZ shall be determined by the SSO/Site Supervisor allowing adequate
space for the activity to be completed, field members and emergency
equipment.
6.2 Contamination Control
6.2.1 Personnel Decontamination Station
Personal hygiene, coupled with diligent decontamination, will significantly
reduce the potential for exposure.
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6.2.2 Minimization of Contact with Contaminants
During completion of all site activities, personnel should attempt to
minimize the chance of contact with contaminated materials. This
involves a conscientious effort to keep "clean" during site activities. All
personnel should minimize kneeling, splash generation, and other
physical contact with contamination as PPE is intended to minimize
accidental contact. This may ultimately minimize the degree of
decontamination required and the generation of waste materials from
site operations.
Field procedures will be developed to control over spray and runoff and
to ensure that unprotected personnel working nearby are not affected.
6.2.3 Personnel Decontamination Sequence
Decontamination will be performed by removing all PPE used in EZ and
placing it in drums/trash cans at the CRZ. Baby wipes shall be available
for wiping hands and face.
6.2.4 Emergency Decontamination
If circumstances dictate that contaminated clothing cannot be readily
removed, then remove gross contamination and wrap injured personnel
with clean garments/blankets to avoid contaminating other personnel or
transporting equipment.
If the injured person can be moved, he/she will be decontaminated by
site personnel as described above before emergency responders handle
the victim. If the person cannot be moved because of the extent of the
injury (a back or neck injury), provisions shall be made to ensure that
emergency response personnel will be able to respond to the victim
without being exposed to potentially hazardous atmospheric conditions.
If the potential for inhalation hazards exist, such as with open excavation,
this area will be covered with polyethylene sheeting to eliminate any
potential inhalation hazards. All emergency personnel are to be
immediately informed of the injured person's condition, potential
contaminants, and provided with all pertinent data.
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6.2.5 Hand-Held Equipment Decontamination
Hand-held equipment includes all monitoring instruments as stated
earlier, samples, hand tools, and notebooks. The hand-held equipment is
dropped at the first decontamination station to be decontaminated by
one of the decontamination team members. These items must be
decontaminated or discarded as waste prior to removal from the CRZ.
To aid in decontamination, monitoring instruments can be sealed in plastic
bags or wrapped in polyethylene. This will also protect the instruments
against contaminants. The instruments will be wiped clean using wipes or
paper towels if contamination is visually evident. Sampling equipment,
hand tools, etc. will be cleaned with non-phosphorous soap to remove any
potentially contaminated soil, and rinsed with deionized water. All
decontamination fluids will be containerized and stored on-site pending
waste characterization sampling and appropriate off-site disposal.
6.3 Communications
The following communications equipment will be utilized as appropriate.
Telephones - A cellular telephone will be located with the SSO/Site Supervisor
for communication with the HSC and emergency support services/facilities.
Hand Signals - Hand signals shall be used by field teams, along with the
buddy system. The entire field team shall know them before operations
commence and their use covered during site-specific training. Typical hand
signals are the following:
Signal Meaning
Hand gripping throat Out of air, can’t breathe
Grip on partner’s wrist or
placement of both hands
around partner’s waist
Leave area immediately, no debate
Hands on top of head Need assistance
Thumbs up Okay, I’m all right, I understand
Thumbs down No, negative
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7.0 MEDICAL SURVEILLANCE
All contractor and subcontractor personnel performing site field work where potential
exposure to contaminants exists are required to have passed a complete medical
surveillance physical examination in accordance with 29 CFR 1910.120(f).
8.0 MEDICAL SURVEILLANCE PROGRAM REQUIREMENTS
A physician's medical clearance for work will be confirmed by the SSO/Site Supervisor
before an employee can work in the EZ. The examination will be completed annually at
a minimum. Additional medical testing may be required by the HSC if, a.) an over-
exposure or accident occurs, b.) an employee exhibits symptoms of exposure, or
c.) other site conditions warrant further medical surveillance.
9.0 EMERGENCY RESPONSE PLAN
This section establishes procedures and provides information for use during a project
emergency. Emergencies happen unexpectedly and quickly, and require an immediate
response; therefore, contingency planning and advanced training of staff is essential.
Specific elements of emergency support procedures that are addressed in the following
subsections include communications, local emergency support units, preparation for
medical emergencies, first aid for injuries incurred on site, record keeping, and
emergency site evacuation procedures.
9.1 Responsibilities
9.1.1 Health and Safety Coordinator (HSC)
The HSC oversees and approves the Emergency Response/Contingency
Plan and performs audits to determine that the plan is in effect and that
all pre-emergency requirements are met. The HSC will be notified of all
incidents, injuries, near misses, OSHA recordable incidents, fires, spills,
releases or equipment damage. The HSC acts as a liaison to applicable
regulatory agencies.
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9.1.2 Site Safety Officer (SSO)
The SSO is responsible for ensuring that all personnel are evacuated
safely and that machinery and processes are shut down or stabilized in
the event of a stop work order or evacuation. The SSO is responsible for
ensuring the HSC are notified of all incidents, all injuries, near misses,
fires, spills, releases or equipment damage. The SSO is required to
immediately notify the HSC of any fatalities or catastrophes (three or
more workers injured and hospitalized) so that the HSC can notify OSHA
within the required time frame.
9.1.3 Emergency Coordinator
The Emergency Coordinator is normally the SSO.
The Emergency Coordinator shall make contact with Local Emergency
Response personnel prior to beginning work on site. In these contacts,
the Emergency Coordinator will inform interested parties about the
nature and duration of work expected on the site and the type of
contaminants and possible health or safety effects of emergencies
involving these contaminants. The Emergency Coordinator shall locate
emergency phone numbers and identify hospital routes prior to beginning
work on the sites. The Emergency Coordinator shall make necessary
arrangements to be prepared for any emergencies that could occur.
The Emergency Coordinator shall implement the Emergency Response/
Contingency Plan whenever conditions resulting from the Site
Investigation warrant such action.
9.1.4 Site Personnel
Project site personnel are responsible for knowing the Emergency
Response/Contingency Plan and the procedures contained herein.
Personnel are expected to notify the Emergency Coordinator of situations
that could constitute a site emergency. Project site personnel, including
all subcontractors will be trained in the Emergency Response/
Contingency Plan.
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9.2 Communications
Once an emergency situation has been stabilized or as soon as practically
possible, the SSO will contact the Langan project manager of any emergency
situation.
9.3 Local Emergency Support Units
In order to be able to deal with any emergency that might occur during
investigative activities at the site, Attachment D will be available in the field
vehicles and provided to all personnel conducting work within the EZ.
Figure 2 shows the hospital route map. Outside emergency number 911 and
local ambulance should be relied on for response to medical emergencies and
transport to emergency rooms. Due to traffic congestion that is prevalent in the
New York metropolitan area, alternate hospital routes will need to be
considered. The Emergency Coordinator will determine the appropriate route
based on time of day and traffic patterns. Changes in the referenced primary
facilities shall be documented with the HASP Field Change Authorization
Request Form (Attachment B).
The Emergency Phone Numbers listed are preliminary. Upon mobilization, the
SSO shall verify all numbers and document the changes in the Site Health and
Safety Logbook. Any changes shall also be documented with the HASP Field
Change Authorization Request Form.
Hospital route maps will be provided to all field personnel.
9.4 Pre-Emergency Planning
Langan will communicate directly with administrative personnel from the
emergency room at the hospital in order to determine whether the hospital has
the facilities and personnel needed to treat cases of trauma resulting from any of
the contaminants expected to be found on the site. Instructions for finding the
hospital will be posted conspicuously in the site office and in each site vehicle.
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Before fieldwork on the site commences, each person who will be working
there or observing the operations will complete a medical data sheet. These data
sheets will be filled out during the initial site safety training meeting and will be
kept on the site.
In the event of an incident where a team member becomes exposed or suffers
from an acute symptom of exposure to site materials and has to be taken to a
hospital, a copy of his/her medical data sheet will be presented to the attending
physician.
9.5 Emergency Medical Treatment
The procedures and rules in this HASP are designed to prevent employee injury.
However, should an injury occur, no matter how slight, it will be reported to the
SSO on site immediately. First-aid equipment will be available on site at the
following locations:
First Aid Kit: Vehicles
Emergency Eye Wash: Vehicles
During the site safety briefing, project personnel will be informed of the location of
the first aid station(s) that has been set up. Unless they are in immediate danger,
severely injured persons will not be moved until paramedics can attend to them.
Some injuries, such as severe cuts and lacerations or bums, may require
immediate treatment. Any first aid instructions that can be obtained from doctors
or paramedics, before an emergency-response squad arrives at the site or before
the injured person can be transported to the hospital, will be followed closely.
Personnel with current first aid and CPR certification will be identified.
Only in non-emergency situations will an injured person be transported to the
hospital by means other than an ambulance.
Nearest hospital: Long Island College Hospital
339 Hicks Street
Brooklyn, NY 11201
(718) 780-1000
(directions from site to hospital found on Figure 2)
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9.6 Emergency Site Evacuation Routes and Procedures
All project personnel will be instructed on proper emergency response
procedures and locations of emergency telephone numbers during the initial site
safety meeting. If an emergency occurs as a result of the site investigation
activities, including but not limited to fire, explosion or significant release of toxic
gas into the atmosphere, the Langan Project Manager will be verbally notified
immediately. All heavy equipment will be shut down and all personnel will
evacuate the work areas and assemble at the nearest intersection to be
accounted for and to receive further instructions.
9.7 Fire Prevention and Protection
In the event of a fire or explosion, procedures will include immediately
evacuating the site and notification of the Langan Project Manager of the
investigation activities. Portable fire extinguishers will be provided at the work
zone. The extinguishers located in the various locations should also be identified
prior to the start of work. No personnel will fight a fire beyond the stage where
it can be put out with a portable extinguisher (incipient stage).
9.7.1 Fire Prevention
Fires will be prevented by adhering to the following precautions:
Good housekeeping and storage of materials.
Storage of flammable liquids and gases away from oxidizers.
Shutting off engines to refuel.
Grounding and bonding metal containers during transfer of flammable
liquids.
Use of UL approved flammable storage cans.
Fire extinguishers rated at least 10 pounds ABC located on all heavy
equipment, in all trailers and near all hot work activities.
The person responsible for the control of fuel source hazards and the
maintenance of fire prevention and/or control equipment is the SSO.
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9.8 Significant Vapor Release
Based on the proposed tasks, the potential for a significant vapor is low.
However, if a release occurs, the following steps will be taken:
Move all personnel to an upwind location. All non-essential personnel shall
evacuate.
Upgrade to Level C Respiratory Protection.
Downwind perimeter locations shall be monitored for volatile organics..
If the release poses a potential threat to human health or the environment in
the community, the Emergency Coordinator shall notify the Langan Project
Manager.
Local emergency response coordinators will be notified.
9.9 Overt Chemical Exposure
The following are standard procedures to treat chemical exposures. Other,
specific procedures detailed on the Material Safety Data Sheet (MSDS) will be
followed, when necessary.
SKIN AND EYE: Use copious amounts of soap and water from eye-wash
kits and portable hand wash stations.
CONTACT: Wash/rinse affected areas thoroughly, then provide
appropriate medical attention. Eyes shall be rinsed for,
minimally, 15 minutes upon chemical contamination. Skin
shall also be rinsed for 15 minutes if contact with caustics,
acids or hydrogen peroxide occurs. Affected items of
clothing shall also be removed from contact with skin.
Providing wash water and soap will be the responsibility of each individual
contractor or subcontractor on-site.
9.10 Decontamination During Medical Emergencies
If emergency life-saving first aid and/or medical treatment is required, normal
decontamination procedures may need to be abbreviated or omitted. The SSO or
27
designee will accompany contaminated victims to the medical facility to advise
on matters involving decontamination when necessary. The outer garments can
be removed if they do not cause delays, interfere with treatment or aggravate
the problem. Respiratory equipment must always be removed. Protective
clothing can be cut away. If the outer contaminated garments cannot be safely
removed on site, a plastic barrier placed between the injured individual and clean
surfaces should be used to help prevent contamination of the inside of
ambulances and/or medical personnel. Outer garments may then be removed at
the medical facility. No attempt will be made to wash or rinse the victim if
his/her injuries are life threatening, unless it is known that the individual has
been contaminated with an extremely toxic or corrosive material which could
also cause severe injury or loss of life to emergency response personnel. For
minor medical problems or injuries, the normal decontamination procedures will
be followed.
9.11 Incident Reporting
Once first aid and/or emergency response needs have been met, the following
parties are to be contacted:
Langan Health and Safety Manager, Tony Moffa (215-491-6500)
Langan Project Manager, Chris McMahon or Steve Ciambruschini
(201-794-6900)
The employer of any injured worker who is not a Langan employee
For emergencies involving personal injury and/or exposure including near-
misses, the SSO or designee will complete and submit an Incident Report form
(Attachment H) within 48 hours. If the employee involved is not a Langan
employee, his employer shall receive a copy of the report.
9.12 Adverse Weather Conditions
In the event of adverse weather conditions, the SSO/Site Supervisor will
determine if work will continue without potentially risking the safety of all field
workers. Some of the items to be considered prior to determining if work should
continue are:
28
Potential for heat stress and heat-related injuries.
Potential for cold stress and cold-related injuries.
Treacherous weather-related working conditions (hail, rain, snow, ice, high
winds).
Limited visibility (fog).
Potential for electrical storms.
Earthquakes.
Other major incidents.
Site activities will be limited to daylight hours, or when suitable artificial light is
provided, and acceptable weather conditions prevail. The SSO will determine the
need to cease field operations or observe daily weather reports and evacuate, if
necessary, in case of severe inclement weather conditions.
9.13 Spill Control and Response
All small spills/environmental releases shall be contained as close to the source
as possible. Whenever possible, the MSDS will be consulted to assist in
determining proper waste characterization and the best means of containment
and cleanup. For small spills, sorbent materials such as sand, sawdust or
commercial sorbents should be placed directly on the substance to contain the
spill and aid recovery. Any acid spills should be diluted or neutralized carefully
prior to attempting recovery. Berms of earthen or sorbent materials can be used
to contain the leading edge of the spills. All spill containment materials will be
properly disposed. An exclusion zone of 50 to 100 feet around the spill area
should be established depending on the size of the spill.
All contractor vehicles shall have spill kits on them with enough material to
contain and absorb the worst-case spill from that vehicle. All vehicles and
equipment shall be inspected prior to be admitted on site. Any vehicle or piece
of equipment that develops a leak will be taken out of service and removed from
the job site.
All subcontractor employees as well as Langan employees will be 40-hour
HAZWOPER trained.
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The following seven steps shall be taken by the Emergency Coordinator:
1. Determine the nature, identity and amounts of major spills.
2. Make sure all unnecessary persons are removed from the spill area.
3. Notify the Site Supervisor or SSO immediately.
4. Use proper PPE in consultation with the SSO/Site Supervisor.
5. If a flammable liquid, gas or vapor is involved, remove all ignition sources
and use non-sparking and/or explosion-proof equipment to contain or clean
up the spill (diesel-only vehicles, air-operated pumps, etc.)
6. If possible, try to stop the leak with appropriate material.
7. Remove all surrounding materials that can react or compound with the
spill.
In addition to the spill control and response procedures described in this HASP,
Langan personnel will coordinate with the designated project manager relative to
spill response and control actions. Notification to the Project Manager must be
immediate and, to the extent possible, include the following information:
Time and location of the spill.
Type and nature of the material spilled.
Amount spilled.
Whether the spill has affected or has a potential to affect a waterway or
sewer.
A brief description of affected areas/equipment.
Whether the spill has been contained.
Expected time of cleanup completion. If spill cleanup cannot be handled by
Langan's on-site personnel alone, such fact must be conveyed to the Project
Manager immediately.
Langan shall not make any notification of spills to outside agencies. The client
will notify regulatory agencies as per their reporting procedures.
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9.14 Emergency Equipment
The following minimum emergency equipment shall be kept and maintained on
site:
Industrial first aid kit.
Fire extinguishers (one per site).
Absorbent material.
9.15 Restoration and Salvage
After an emergency, prompt restoration of utilities, fire protection equipment,
medical supplies and other equipment will reduce the possibility of further
losses. Some of the items that may need to be addressed are:
Refilling fire extinguishers.
Refilling medical supplies.
Recharging eyewashes and/or showers.
Replenishing spill control supplies.
10.0 TRAINING
10.1 General Health and Safety Training
With Langan corporate policy, and pursuant to 29 CFR 1910.120, hazardous
waste site workers shall, at the time of job assignment, have received a
minimum of 40 hours of initial health and safety training for hazardous waste site
operations unless otherwise noted in the above reference. At a minimum, the
training shall have consisted of instruction in the topics outlined in the standard.
Personnel who have not satisfied the requirements for initial training shall not be
allowed to work in any site activities in which they may be exposed to hazards
(chemical or physical).
10.2 Annual Eight-Hour Refresher Training
Annual eight-hour refresher training will be required of all hazardous waste site
field personnel in order to maintain their qualifications for site work. The training
31
will cover a review of 1910.120 requirements and related company programs
and procedures. The SSO will be required to have the eight-hour HAZWOPER
supervisor training.
10.3 Site-Specific Training
Prior to commencement of site activities, all field personnel assigned to the
project will have completed training that will specifically address the activities,
procedures, monitoring, and equipment used in the site operations. It will
include a documented verbal review of the entire HASP and all the provisions
within the HASP document. Should any new employees arrive on-site, they will
also be given a documented full HASP review ‟ or one that address the
appropriate tasks that remain at the time of the new employee’s arrival.
10.4 Onsite Safety Briefings
Project personnel and visitors will participate in documented daily on-site health
and safety briefings (“Tailgate Talks”) led by the SSO/Site Supervisor to assist
site personnel in safely conducting their work activities. The briefings will include
information on operations to be conducted that shift, changes in work practices
or changes in the site's environmental conditions, as well as periodic
reinforcement of previously discussed topics. The briefings will also provide a
forum to facilitate conformance with safety requirements and to identify
performance deficiencies related to safety during daily activities or as a result of
safety inspections. The meetings will also be an opportunity for the work crews
to be updated on monitoring results. Prior to starting any new activity, a training
session will be held for crew members involved in the activity. The Safety
Briefing form (Attachment I) can be used to facilitate this effort.
10.5 First Aid and CPR
The SSO will identify those individuals with first aid and CPR training in order to
ensure that emergency medical treatment is available during field activities. The
training will be consistent with the requirements of the American Red Cross or
the National Safety Council.
32
10.6 Hazard Communication
All material brought on-site will be in the appropriate containers and will be
properly labeled. The MSDS for unleaded gasoline, diesel fuel, and hydraulic
fluid are attached. Langan’s written Hazard Communication program, in
compliance with 29 CFR 1910.1200, is maintained in Langan’s office in
Elmwood Park, New Jersey.
11.0 RECORDKEEPING
The following is a summary of required health and safety logs, reports and
recordkeeping.
11.1 Field Change Authorization Request
A field change authorization request is to be completed for requesting a change
to this HASP (Attachment B). Any changes to the work to be performed that is
not included in the HASP will require an Addendum that is approved by the
Langan Project Manager and Langan HSC to be prepared. Approved changes
will be reviewed with all field personnel at a safety briefing.
11.2 Medical and Training Records
Copies or verification of training (40-hour, 8-hour, supervisor, site-specific
training, documentation of three-day OJT, and respirator fit-test records) and
medical clearance for Site work and respirator use will be maintained in the
office and available upon request. Records for all subcontractor employees must
also be available upon request. All employee medical records will be maintained
by the HSC.
11.3 Onsite Log
A log of personnel on site each day will be kept by the SSO or designee.
11.4 Daily Safety Meetings (“Tailgate Talks”)
Completed Safety Briefing forms will be maintained by the SSO.
33
11.5 Exposure Records
All personal monitoring results, laboratory reports, calculations and air sampling
data sheets are part of an employee exposure record. These records will be
maintained by the SSO/Site Supervisor during site work. At the end of the
project they will be maintained according to 29 CFR 1910.1020.
11.6 Incident Reports
The incident reporting and investigation during site work will follow the
procedures specified here in.
11.7 OSHA Form 300
An OSHA Form 300 will be kept at the Langan Office in Doylestown,
Pennsylvania. All recordable injuries or illnesses will be recorded on this form.
Subcontractor employers must also meet the requirements of maintaining an
OSHA 300 form. The Incident Report form used to capture the details of work-
related injuries/illnesses meets the requirements of the OSHA Form 301
(supplemental record) and must be maintained with the OSHA Form 300 for all
recordable injuries or illnesses.
11.8 Hazard Communication Program/MSDS
Material Safety Data Sheets (MSDS) have been obtained for applicable
substances and are included in this EHS Plan (Attachment A). Langan’s written
Hazard Communication program, in compliance with 29 CFR 1910.1200, is
maintained by the HSC in Elmwood Park, New Jersey.
11.9 Work Permits
All work permits, including, but not limited to, street-opening, hot work,
lockout/tagout, and line-breaking permits will be maintained in the project files.
34
12.0 FIELD PERSONNEL REVIEW
This form serves as documentation that field personnel have been verbally given a full
HASP review by Langan personnel, and understand the provisions of this EHS Plan. It is
maintained on site by the SSO as a project record.
Each field team member shall sign this section after Site-specific training is completed
and before being permitted to work onsite.
35
I have been given a verbal full HASP review by Langan personnel and understand the
information presented. I will comply with the provisions contained herein.
Name (Print and Sign) Company Date
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Bond Street & 400 Carroll Street (2013-07-10).doc
TABLE 1
SUSPECTED CONTAMINANTS OF CONCERN
363 BOND STREET & 400 CARROLL STREET
BROOKLYN, NEW YORK
1 of 1
Contaminant Of Concern
Affected Media
VOLATILES
Benzene Soil Vapor / Soil / Groundwater
Ethylbenzene Soil Vapor / Soil / Groundwater
n�propylbenzene Soil Vapor / Soil / Groundwater
MTBE Soil Vapor / Soil / Groundwater
Toluene Soil Vapor / Soil / Groundwater
Xylenes Soil Vapor / Soil / Groundwater
SEMI�VOLATILES
Common Historic Fill Contaminants:
Benzo(a)anthracene Soil / Groundwater
Benzo(b)flouranthene Soil / Groundwater
Benzo(k)flouranthene Soil / Groundwater
Benzo(a)pyrene Soil / Groundwater
Chrysene Soil / Groundwater
Indeno(1,2,3�cd)pyrene Soil / Groundwater
PESTICIDES / PCBs
Miscellaneous TBD Soil Vapor / Soil / Groundwater
METALS
Miscellaneous TBD Soil / Groundwater
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Contaminants of Concern.doc
TABLE 2
SELECTED POTENTIAL CHEMICAL EXPOSURE LIMITS AND HEALTH EFFECTS
363 BOND STREET & 400 CARROLL STREET
BROOKLYN, NEW YORK
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Limits.doc
1 of 4
Chemical Permissible
Exposure Limit
IDLH Limit Exposure Routes Exposure Symptoms
Benzene 1 ppm 50 ppm Inhalation, Skin
Absorption, Ingestion,
skin and/or eye contact
Irritate eyes, skin, nose; respiratory
system; giddiness; head, nausea,
staggered gait; fatigue, anorexia,
lassitude; dermatitis; bone marrow
depression; [carcinogenic]
Toluene 200 ppm 500 ppm Inhalation, Skin
Absorption, Ingestion,
skin and/or eye contact
Irritate eyes, nose; fatigue,
weakness, confusion, euphoria,
dizziness, headache; dilated pupils,
lacrimation; nervousness, muscle
fatigue, insomnia; paresthesia;
dermatitis; liver, kidney damage;
mucous membrane; narcosis, coma
Ethylbenzene 100 ppm 800 ppm (10% LEL) Inhalation, Ingestion,
skin and/or eye contact
Irritate eyes, skin, mucous
membrane ;headache, dermatitis;
narcosis, coma
Methyl Tert�Butyl Ether
(MTBE)
None Established 1.6% Inhalation, Ingestion,
skin and/or eye contact
Irritate eyes, skin, respiratory tract,
kidney damage, headache, depress
nervouse central system, nausea,
vomiting, dizziness, loss of
consciousness, liver damage,
lymphomas, leukemias, may cause
cancer
Xylenes 100 ppm 900 ppm Inhalation, Skin
Absorption, Ingestion,
skin and/or eye contact
Irritate eyes, skin, nose, throat;
dizziness, excitement, drowsiness,
incoordination, staggering gait; corn
vacuolization; anorexia, nausea,
vomit, abdominal pain; dermatitis
TABLE 2
SELECTED POTENTIAL CHEMICAL EXPOSURE LIMITS AND HEALTH EFFECTS
363 BOND STREET & 400 CARROLL STREET
BROOKLYN, NEW YORK
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Limits.doc
2 of 4
Chemical Permissible
Exposure Limit
IDLH Limit Exposure Routes Exposure Symptoms
Total Volatile Organics 15 ppm 150 ppm Inhalation, Skin
Absorption, Ingestion
Irritation eyes, skin, nose, throat,
respiratory system; nausea; flush
face, neck; dizziness,
incoordination; headache,
drowsiness; skin erythema (skin
redness); liver damage; [potential
occupational carcinogen]
Benzo(a)anthracene 0.2 mg/m3 80 mg/m3 Inhalation, Skin
Absorption, Ingestion
Irritate eyes, skin, upper respiratory
system, cough
Benzo(b)fluoranthene 0.2 mg/m3 80 mg/m3 Inhalation, Skin
Absorption, Ingestion
Irritate eyes, skin, upper respiratory
system, cough
Benzo(k)fluoranthene 0.2 mg/m3 80 mg/m3 Inhalation, Skin
Absorption, Ingestion
Irritate eyes, skin, upper respiratory
system, cough
Benzo(a)pyrene 0.2 mg/m3 80 mg/m3 Inhalation, Skin
Absorption, Ingestion
Irritate eyes, skin, upper respiratory
system, cough
Chrysene 0.2 mg/m3 80 mg/m3 Inhalation, Skin
Absorption, Ingestion
Irritate eyes, skin, upper respiratory
system, cough
Indeno (1,2,3�cd) pyrene 0.2 mg/m3 80 mg/m3 Inhalation, Skin
Absorption, Ingestion
Irritate eyes, skin, upper respiratory
system, cough
Pesticides 1 mg/m3 500 mg/m3 Inhalation, Skin
Absorption, Ingestion,
skin and/or eye contact
Irritation eyes, skin; paresthesia
tongue, lips, face; tremor; anxiety,
dizziness, confusion, malaise
(vague feeling of discomfort),
headache, lassitude (weakness,
exhaustion); convulsions; paresis
hands; vomiting; [potential
occupational carcinogen]
TABLE 2
SELECTED POTENTIAL CHEMICAL EXPOSURE LIMITS AND HEALTH EFFECTS
363 BOND STREET & 400 CARROLL STREET
BROOKLYN, NEW YORK
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Limits.doc
3 of 4
Chemical Permissible
Exposure Limit
IDLH Limit Exposure Routes Exposure Symptoms
Lead
0.05 mg/mg3 100 mg/mg3 Inhalation, Ingestion,
Skin and/or Eye Contact
Lassitude (weakness, exhaustion),
insomnia; facial pallor; anorexia,
weight loss, malnutrition;
constipation, abdominal pain, colic;
anemia; gingival lead line; tremor;
paralysis wrist, ankles;
encephalopathy; kidney disease;
irritation eyes; hypertension
Arsenic
0.010 mg/m3
5 mg/m3
Inhalation, Ingestion,
Skin Absorption, Skin
and/or Eye Contact
Ulceration of nasal septum,
dermatitis, gastrointestinal
disturbances, peripheral
neuropathy, resp irritation,
hyperpigmentation of skin,
[potential occupational carcinogen]
Hexavalent Chromium
5 mg/m3 250 mg/m3 Inhalation, Ingestion,
Skin and/or Eye Contact
Irritation eyes, skin; lung fibrosis
(histologic)
Total Chromium
5 mg/m3 250 mg/m3 Inhalation, Ingestion,
Skin and/or Eye Contact
Irritation eyes, skin; lung fibrosis
(histologic)
Mercury
0.1 mg/m3 10 mg/m3 Inhalation, Ingestion,
Skin Absorption, Skin
and/or Eye Contact
Irritation eyes, skin; cough, chest
pain, dyspnea (breathing difficulty),
bronchitis, pneumonitis; tremor,
insomnia, irritability, indecision,
headache, lassitude (weakness,
exhaustion); stomatitis, salivation;
gastrointestinal disturbance,
anorexia, weight loss; proteinuria
Copper 1 mg/m3 100 mg/m3 Inhalation, Ingestion,
skin and/or eye contact
Irritation eyes, respiratory system;
cough, dyspnea (breathing
difficulty), wheezing; [potential
occupational carcinogen]
TABLE 2
SELECTED POTENTIAL CHEMICAL EXPOSURE LIMITS AND HEALTH EFFECTS
363 BOND STREET & 400 CARROLL STREET
BROOKLYN, NEW YORK
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Limits.doc
4 of 4
Chemical Permissible
Exposure Limit
IDLH Limit Exposure Routes Exposure Symptoms
Nickel 1 mg/m3 10 mg/m3 Inhalation, Skin
Absorption, Ingestion,
skin and/or eye contact
Irritation eyes, skin; cough, chest
pain, dyspnea (breathing difficulty),
bronchitis, pneumonitis; tremor,
insomnia, irritability, indecision,
headache, lassitude (weakness,
exhaustion); stomatitis, salivation;
gastrointestinal disturbance,
anorexia, weight loss; proteinuria
--- No exposure limits listed in the NIOSH Pocket Guide to Chemical Hazards dated November 2010.
Page 1 of 1
TABLE 3
HAZARD ANALYSIS
363 BOND STREET & 400 CARROLL STREET
BROOKLYN, NEW YORK
Potential Hazard
Utility
Markout
Surveying
Drilling
Groundwater Sampling
Inhalation of
volatiles
low
low
low to moderate
low to moderate
Skin and eye
contact
low to moderate
low to moderate
moderate to high
moderate to high
Ingestion
low
low
low to moderate
low to moderate
Inhalation of dust
low low
moderate low
Heat stress
depends on
temperature
depends on
temperature
depends on
temperature
depends on
temperature
Cold stress
depends on
temperature
depends on
temperature
depends on
temperature
depends on
temperature
Confined Space
Entry
not applicable
not applicable
not applicable
not applicable
Heavy equipment
low low
moderate to high low
Noise
low low
moderate to high
low
Tripping
moderate
moderate
moderate
moderate
PPE
low low
low to moderate
low to moderate
Utilities
low
low
moderate
low
Other Physical
hazards
moderate
moderate
moderate to high
moderate
Biological hazards
low
low
low
low
Flammable
hazards
low
low
low
low
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Carroll)\Appendix D 2 HASP\Tables\HASP TABLE 3 2 Hazard Analysis.doc
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(363 Bond�400 Carroll)\Appendix D � HASP\Tables\HASP TABLE 4 � Action Levels.doc
Page 1 of 1
TABLE 4
INSTRUMENTATION ACTION LEVELS
363 BOND STREET & 400 CARROLL STREET
BROOKLYN, NEW YORK
Instrument Action Level Level of Protection /
Action Required
PID*/FID* < 10 ppm within AOC zone Level D
> 10 ppm (initial) Stop work. Resume work
once readings are below 15
ppm.
> 10 ppm and < 30 ppm
(steady state condition) within
breathing zone
Level C/Initiate Perimeter
Monitoring
> 30 ppm (steady state
condition) within AOC zone
Stop Work / Suppress
Emissions / Evacuate and re�
evaluate.
>10 ppm sustained for 1
minute at AOC site boundary.
Stop Work / Backfill source of
emissions and re�evaluate.
BKD = Background concentration
*PID/FID readings are taken at personnel breathing zone height using a 10.2V lamp PID or
equivalent.
Page 1 of 1
TABLE 5
PERSONAL PROTECTIVE EQUIPMENT
363 BOND STREET & 400 CARROLL STREET
BROOKLYN, NEW YORK
Respiratory Protection: Level D:
No respirator required.
Level C: Half�face, Air Purifying Respirator (APR) with combination HEPA
(dusts, fumes, aerosols) and organic vapor cartridges. The respirator
will be NIOSH�approved. Level C � supplemental
by task
Fullface, Air Purifying Respirator (APR) with combination HEPA
(dusts, fumes, aerosols), acid gas, organic vapor cartridges. The
respirator will be NIOSH�approved.
Personal Protective Clothing: Level D:
Hard�hat, traffic vest (if working on or adjacent to the roadway), long
sleeve work shirt & work pants of natural fibers, safety glasses or
goggles, steel�toed boots, hearing protection (if needed), nitril inner
gloves and leather outer gloves. Level D � supplemental
PPE by task
Tyvek disposal suit
Level C:
Chemically resistant outer boots and Chemical resistant Tyvek
disposal suite.
\\LANGAN.COM\DATA\EP\DATA5\100287501\ENGINEERING DATA\ENVIRONMENTAL\REPORTS\2013�07 � OER PHASE II RIWP REVISED (363 BOND�
400 CARROLL)\APPENDIX D � HASP\TABLES\HASP TABLE 5 � PPE.DOC
Project Drawing Title
KINGS COUNTY NEW YORK
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BLOCK No. 452, LOT Nos. 1 & 15
BROOKLYN
pfqb=il`^qflkj^m
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© 2
01
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ga
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Project No.
Date
Scale
Drawn By
Last Revised
Figure
100287501
10/19/2012
amf
6/14/2013
SITE
Copyright:© 2013 National Geographic Society, i-cubed
.
1"=2000'
1
2,000 0 2,000
SCALE IN FEET
619 River Drive Center 1Elmwood Park, NJ 07407-1338
T: 201.794.6900 F: 201.794.0366www.langan.com
NEW JERSEY NEW YORK VIRGINIA CALIFORNIA PENNSYLVANIA CONNECTICUT FLORIDA
ABU DHABI ATHENS DOHA
DUBAI ISTANBUL
NJ CERTIFICATE OF AUTHORIZATION No. 24GA27996400
Emergency Route to Long Island College Hospital (Phone # (718) 780-1000 :
1 Start traveling northeast on Bond Street toward 1st Street
2 Turn Left onto Sackett Street
3 Turn right onto Hicks Street
5 Arrive at Long Island College Hospital, 339 Hicks Street, Brooklyn NY 11201
MAP REFERENCE: Google Maps
Project
Manhattan New York
ELMWOOD PK, NJ NEW YORK, NY PHILADELPHIA, PA DOYLESTOWN , PA NEW HAVEN, CT MIAMI, FL PROJECT NO. DATE SCALE FIGURE NO.
(201) 794-6900 (212) 964-7888 (215) 864-0640 (215) 348-7101 (203) 562-5771 (305) 362-1166 100287501 8/10/2012 NTS 2
363-365 BOND STREET & 400 CARROLL STREET
EMERGENGY HOSPITAL ROUTE MAPLangan Engineering and Environmental Services
\\langan.com\data\EP\data5\100287501\Engineering Data\Environmental\Reports\2012-10 OER Phase II RIWP\Appendix C - HASP\Figures\Figure 2 - Hospital Route/Figure 2 - Hospital Route
MATERIAL SAFETY DATA SHEET Diesel Fuel (All Types) MSDS No. 9909
Revision Date: 10/18/2006 Page 1 of 7
EMERGENCY OVERVIEW CAUTION!
OSHA/NFPA COMBUSTIBLE LIQUID - SLIGHT TO MODERATE IRRITANT EFFECTS CENTRAL NERVOUS SYSTEM HARMFUL OR FATAL IF SWALLOWED
Moderate fire hazard. Avoid breathing vapors or mists. May cause dizziness and drowsiness. May cause moderate eye irritation and skin irritation (rash). Long-term, repeated exposure may cause skin cancer. If ingested, do NOT induce vomiting, as this may cause chemical pneumonia (fluid in the lungs).
NFPA 704 (Section 16)
1. CHEMICAL PRODUCT AND COMPANY INFORMATION
Hess Corporation 1 Hess Plaza Woodbridge, NJ 07095-0961
EMERGENCY TELEPHONE NUMBER (24 hrs): CHEMTREC (800) 424-9300 COMPANY CONTACT (business hours): Corporate Safety (732) 750-6000 MSDS INTERNET WEBSITE: www.hess.com (See Environment, Health, Safety & Social Responsibility)
SYNONYMS: Ultra Low Sulfur Diesel (ULSD); Low Sulfur Diesel; Motor Vehicle Diesel Fuel; Diesel Fuel #2; Dyed Diesel Fuel; Non-Road, Locomotive and Marine Diesel Fuel; Tax-exempt Diesel Fuel
See Section 16 for abbreviations and acronyms. 2. COMPOSITION and CHEMICAL INFORMATION ON INGREDIENTS
INGREDIENT NAME (CAS No.) CONCENTRATION PERCENT BY WEIGHT Diesel Fuel (68476-34-6) 100 Naphthalene (91-20-3) Typically < 0.01 A complex mixture of hydrocarbons with carbon numbers in the range C9 and higher. Diesel fuel may be dyed (red) for tax purposes. May contain a multifunctional additive.
3. HAZARDS IDENTIFICATION EYESContact with liquid or vapor may cause mild irritation.
SKINMay cause skin irritation with prolonged or repeated contact. Practically non-toxic if absorbed following acute (single) exposure. Liquid may be absorbed through the skin in toxic amounts if large areas of skin are repeatedly exposed.
INGESTIONThe major health threat of ingestion occurs from the danger of aspiration (breathing) of liquid drops into the lungs, particularly from vomiting. Aspiration may result in chemical pneumonia (fluid in the lungs), severe lung damage, respiratory failure and even death.
Ingestion may cause gastrointestinal disturbances, including irritation, nausea, vomiting and diarrhea, and central nervous system (brain) effects similar to alcohol intoxication. In severe cases, tremors, convulsions, loss of consciousness, coma, respiratory arrest, and death may occur.
MATERIAL SAFETY DATA SHEET Diesel Fuel (All Types) MSDS No. 9909
Revision Date: 10/18/2006 Page 2 of 7
INHALATIONExcessive exposure may cause irritations to the nose, throat, lungs and respiratory tract. Central nervous system (brain) effects may include headache, dizziness, loss of balance and coordination, unconsciousness, coma, respiratory failure, and death.
WARNING: the burning of any hydrocarbon as a fuel in an area without adequate ventilation may result in hazardous levels of combustion products, including carbon monoxide, and inadequate oxygen levels, which may cause unconsciousness, suffocation, and death.
CHRONIC EFFECTS and CARCINOGENICITYSimilar products produced skin cancer and systemic toxicity in laboratory animals following repeated applications. The significance of these results to human exposures has not been determined - see Section 11 Toxicological Information.
IARC classifies whole diesel fuel exhaust particulates as probably carcinogenic to humans (Group 2A). NIOSH regards whole diesel fuel exhaust particulates as a potential cause of occupational lung cancer based on animal studies and limited evidence in humans.
MEDICAL CONDITIONS AGGRAVATED BY EXPOSURE Irritation from skin exposure may aggravate existing open wounds, skin disorders, and dermatitis (rash).
4. FIRST AID MEASURES EYESIn case of contact with eyes, immediately flush with clean, low-pressure water for at least 15 min. Hold eyelids open to ensure adequate flushing. Seek medical attention.
SKINRemove contaminated clothing. Wash contaminated areas thoroughly with soap and water or waterless hand cleanser. Obtain medical attention if irritation or redness develops.
INGESTIONDO NOT INDUCE VOMITING. Do not give liquids. Obtain immediate medical attention. If spontaneous vomiting occurs, lean victim forward to reduce the risk of aspiration. Monitor for breathing difficulties. Small amounts of material which enter the mouth should be rinsed out until the taste is dissipated.
INHALATIONRemove person to fresh air. If person is not breathing provide artificial respiration. If necessary, provide additional oxygen once breathing is restored if trained to do so. Seek medical attention immediately.
5. FIRE FIGHTING MEASURES FLAMMABLE PROPERTIES: FLASH POINT: > 125 oF (> 52 oC) minimum PMCC AUTOIGNITION POINT: 494 oF (257 oC) OSHA/NFPA FLAMMABILITY CLASS: 2 (COMBUSTIBLE) LOWER EXPLOSIVE LIMIT (%): 0.6 UPPER EXPLOSIVE LIMIT (%): 7.5
FIRE AND EXPLOSION HAZARDS Vapors may be ignited rapidly when exposed to heat, spark, open flame or other source of ignition. When mixed with air and exposed to an ignition source, flammable vapors can burn in the open or explode in confined spaces. Being heavier than air, vapors may travel long distances to an ignition source and flash back. Runoff to sewer may cause fire or explosion hazard.
EXTINGUISHING MEDIA SMALL FIRES: Any extinguisher suitable for Class B fires, dry chemical, CO2, water spray, fire fighting foam, or Halon.
MATERIAL SAFETY DATA SHEET Diesel Fuel (All Types) MSDS No. 9909
Revision Date: 10/18/2006 Page 3 of 7
LARGE FIRES: Water spray, fog or fire fighting foam. Water may be ineffective for fighting the fire, but may be used to cool fire-exposed containers.
FIRE FIGHTING INSTRUCTIONS Small fires in the incipient (beginning) stage may typically be extinguished using handheld portable fire extinguishers and other fire fighting equipment.
Firefighting activities that may result in potential exposure to high heat, smoke or toxic by-products of combustion should require NIOSH/MSHA- approved pressure-demand self-contained breathing apparatus with full facepiece and full protective clothing.
Isolate area around container involved in fire. Cool tanks, shells, and containers exposed to fire and excessive heat with water. For massive fires the use of unmanned hose holders or monitor nozzles may be advantageous to further minimize personnel exposure. Major fires may require withdrawal, allowing the tank to burn. Large storage tank fires typically require specially trained personnel and equipment to extinguish the fire, often including the need for properly applied fire fighting foam.
See Section 16 for the NFPA 704 Hazard Rating.
6. ACCIDENTAL RELEASE MEASURES ACTIVATE FACILITY’S SPILL CONTINGENCY OR EMERGENCY RESPONSE PLAN.
Evacuate nonessential personnel and remove or secure all ignition sources. Consider wind direction; stay upwind and uphill, if possible. Evaluate the direction of product travel, diking, sewers, etc. to confirm spill areas. Spills may infiltrate subsurface soil and groundwater; professional assistance may be necessary to determine the extent of subsurface impact.
Carefully contain and stop the source of the spill, if safe to do so. Protect bodies of water by diking, absorbents, or absorbent boom, if possible. Do not flush down sewer or drainage systems, unless system is designed and permitted to handle such material. The use of fire fighting foam may be useful in certain situations to reduce vapors. The proper use of water spray may effectively disperse product vapors or the liquid itself, preventing contact with ignition sources or areas/equipment that require protection.
Take up with sand or other oil absorbing materials. Carefully shovel, scoop or sweep up into a waste container for reclamation or disposal - caution, flammable vapors may accumulate in closed containers. Response and clean-up crews must be properly trained and must utilize proper protective equipment (see Section 8).
7. HANDLING and STORAGE HANDLING PRECAUTIONS Handle as a combustible liquid. Keep away from heat, sparks, and open flame! Electrical equipment should be approved for classified area. Bond and ground containers during product transfer to reduce the possibility of static-initiated fire or explosion.
Diesel fuel, and in particular low and ultra low sulfur diesel fuel, has the capability of accumulating a static electrical charge of sufficient energy to cause a fire/explosion in the presence of lower flashpoint products such as gasoline. The accumulation of such a static charge occurs as the diesel flows through pipelines, filters, nozzles and various work tasks such as tank/container filling, splash loading, tank cleaning; product sampling; tank gauging; cleaning, mixing, vacuum truck operations, switch loading, and product agitation. There is a greater potential for static charge accumulation in cold temperature, low humidity conditions.
Documents such as 29 CFR OSHA 1910.106 "Flammable and Combustible Liquids, NFPA 77 Recommended Practice on Static Electricity, API 2003 "Protection Against Ignitions Arising Out of Static, Lightning, and Stray Currents and ASTM D4865 "Standard Guide for Generation and Dissipation of Static
MATERIAL SAFETY DATA SHEET Diesel Fuel (All Types) MSDS No. 9909
Revision Date: 10/18/2006 Page 4 of 7
Electricity in Petroleum Fuel Systems" address special precautions and design requirements involving loading rates, grounding, bonding, filter installation, conductivity additives and especially the hazards associated with "switch loading." ["Switch Loading" is when a higher flash point product (such as diesel) is loaded into tanks previously containing a low flash point product (such as gasoline) and the electrical charge generated during loading of the diesel results in a static ignition of the vapor from the previous cargo (gasoline).]
Note: When conductivity additives are used or are necessary the product should achieve 25 picosiemens/meter or greater at the handling temperature.
STORAGE PRECAUTIONS Keep away from flame, sparks, excessive temperatures and open flame. Use approved vented containers. Keep containers closed and clearly labeled. Empty product containers or vessels may contain explosive vapors. Do not pressurize, cut, heat, weld or expose such containers to sources of ignition.
Store in a well-ventilated area. This storage area should comply with NFPA 30 "Flammable and Combustible Liquid Code". Avoid storage near incompatible materials. The cleaning of tanks previously containing this product should follow API Recommended Practice (RP) 2013 "Cleaning Mobile Tanks In Flammable and Combustible Liquid Service" and API RP 2015 "Cleaning Petroleum Storage Tanks".
WORK/HYGIENIC PRACTICES Emergency eye wash capability should be available in the near proximity to operations presenting a potential splash exposure. Use good personal hygiene practices. Avoid repeated and/or prolonged skin exposure. Wash hands before eating, drinking, smoking, or using toilet facilities. Do not use as a cleaning solvent on the skin. Do not use solvents or harsh abrasive skin cleaners for washing this product from exposed skin areas. Waterless hand cleaners are effective. Promptly remove contaminated clothing and launder before reuse. Use care when laundering to prevent the formation of flammable vapors which could ignite via washer or dryer. Consider the need to discard contaminated leather shoes and gloves.
8. EXPOSURE CONTROLS and PERSONAL PROTECTION EXPOSURE LIMITS Exposure Limits
Components (CAS No.) Source TWA/STEL Note
Diesel Fuel: (68476-34-6) OSHA ACGIH
5 mg/m, as mineral oil mist 100 mg/m3 (as totally hydrocarbon vapor) TWA
A3, skin
Naphthalene (91-20-3) OSHA ACGIH
10 ppm TWA 10 ppm TWA / 15 ppm STEL
A4, Skin
ENGINEERING CONTROLS Use adequate ventilation to keep vapor concentrations of this product below occupational exposure and flammability limits, particularly in confined spaces.
EYE/FACE PROTECTION Safety glasses or goggles are recommended where there is a possibility of splashing or spraying.
SKIN PROTECTION Gloves constructed of nitrile, neoprene, or PVC are recommended. Chemical protective clothing such as of E.I. DuPont TyChem®, Saranex® or equivalent recommended based on degree of exposure. Note: The resistance of specific material may vary from product to product as well as with degree of exposure. Consult manufacturer specifications for further information.
MATERIAL SAFETY DATA SHEET Diesel Fuel (All Types) MSDS No. 9909
Revision Date: 10/18/2006 Page 5 of 7
RESPIRATORY PROTECTION A NIOSH/MSHA-approved air-purifying respirator with organic vapor cartridges or canister may be permissible under certain circumstances where airborne concentrations are or may be expected to exceed exposure limits or for odor or irritation. Protection provided by air-purifying respirators is limited. Refer to OSHA 29 CFR 1910.134, NIOSH Respirator Decision Logic, and the manufacturer for additional guidance on respiratory protection selection.
Use a positive pressure, air-supplied respirator if there is a potential for uncontrolled release, exposure levels are not known, in oxygen-deficient atmospheres, or any other circumstance where an air-purifying respirator may not provide adequate protection.
9. PHYSICAL and CHEMICAL PROPERTIES APPEARANCE Clear, straw-yellow liquid. Dyed fuel oil will be red or reddish-colored.
ODOR Mild, petroleum distillate odor
BASIC PHYSICAL PROPERTIESBOILING RANGE: 320 to 690 oF (160 to 366 oC) VAPOR PRESSURE: 0.009 psia @ 70 oF (21 oC) VAPOR DENSITY (air = 1): > 1.0 SPECIFIC GRAVITY (H2O = 1): 0.83 to 0.88 @ 60 oF (16 oC) PERCENT VOLATILES: 100 % EVAPORATION RATE: Slow; varies with conditions SOLUBILITY (H2O): Negligible
10. STABILITY and REACTIVITY STABILITY: Stable. Hazardous polymerization will not occur.
CONDITIONS TO AVOID and INCOMPATIBLE MATERIALS Avoid high temperatures, open flames, sparks, welding, smoking and other ignition sources. Keep away from strong oxidizers; Viton ®; Fluorel ®
HAZARDOUS DECOMPOSITION PRODUCTS Carbon monoxide, carbon dioxide and non-combusted hydrocarbons (smoke).
11. TOXICOLOGICAL PROPERTIES ACUTE TOXICITY Acute dermal LD50 (rabbits): > 5 ml/kg Acute oral LD50 (rats): 9 ml/kg Primary dermal irritation: extremely irritating (rabbits) Draize eye irritation: non-irritating (rabbits) Guinea pig sensitization: negative
CHRONIC EFFECTS AND CARCINOGENICITY Carcinogenic: OSHA: NO IARC: NO NTP: NO ACGIH: A3
Studies have shown that similar products produce skin tumors in laboratory animals following repeated applications without washing or removal. The significance of this finding to human exposure has not been determined. Other studies with active skin carcinogens have shown that washing the animal’s skin with soap and water between applications reduced tumor formation.
MUTAGENICITY (genetic effects) This material has been positive in a mutagenicity study.
MATERIAL SAFETY DATA SHEET Diesel Fuel (All Types) MSDS No. 9909
Revision Date: 10/18/2006 Page 6 of 7
12. ECOLOGICAL INFORMATION Keep out of sewers, drainage areas, and waterways. Report spills and releases, as applicable, under Federal and State regulations.
13. DISPOSAL CONSIDERATIONS Consult federal, state and local waste regulations to determine appropriate disposal options.
14. TRANSPORTATION INFORMATION PROPER SHIPPING NAME: Diesel Fuel Placard (International Only): HAZARD CLASS and PACKING GROUP: 3, PG III DOT IDENTIFICATION NUMBER: NA 1993 (Domestic) UN 1202 (International) DOT SHIPPING LABEL: None
Use Combustible Placard if shipping in bulk domestically 15. REGULATORY INFORMATION U.S. FEDERAL, STATE, and LOCAL REGULATORY INFORMATION This product and its constituents listed herein are on the EPA TSCA Inventory. Any spill or uncontrolled release of this product, including any substantial threat of release, may be subject to federal, state and/or local reporting requirements. This product and/or its constituents may also be subject to other regulations at the state and/or local level. Consult those regulations applicable to your facility/operation.
CLEAN WATER ACT (OIL SPILLS) Any spill or release of this product to "navigable waters" (essentially any surface water, including certain wetlands) or adjoining shorelines sufficient to cause a visible sheen or deposit of a sludge or emulsion must be reported immediately to the National Response Center (1-800-424-8802) as required by U.S. Federal Law. Also contact appropriate state and local regulatory agencies as required.
CERCLA SECTION 103 and SARA SECTION 304 (RELEASE TO THE ENVIRONMENT) The CERCLA definition of hazardous substances contains a “petroleum exclusion” clause which exempts crude oil, refined, and unrefined petroleum products and any indigenous components of such. However, other federal reporting requirements (e.g., SARA Section 304 as well as the Clean Water Act if the spill occurs on navigable waters) may still apply.
SARA SECTION 311/312 - HAZARD CLASSES ACUTE HEALTH CHRONIC HEALTH FIRE SUDDEN RELEASE OF PRESSURE REACTIVE
X X X -- --
SARA SECTION 313 - SUPPLIER NOTIFICATIONThis product may contain listed chemicals below the de minimis levels which therefore are not subject to the supplier notification requirements of Section 313 of the Emergency Planning and Community Right-To-Know Act (EPCRA) of 1986 and of 40 CFR 372. If you may be required to report releases of chemicals listed in 40 CFR 372.28, you may contact Hess Corporate Safety if you require additional information regarding this product.
CALIFORNIA PROPOSITON 65 LIST OF CHEMICALS This product contains the following chemicals that are included on the Proposition 65 "List of Chemicals" required by the California Safe Drinking Water and Toxic Enforcement Act of 1986:
INGREDIENT NAME (CAS NUMBER) Date ListedDiesel Engine Exhaust (no CAS Number listed) 10/01/1990
CANADIAN REGULATORY INFORMATION (WHMIS) Class B, Division 3 (Combustible Liquid) and Class D, Division 2, Subdivision B (Toxic by other means)
MATERIAL SAFETY DATA SHEET Diesel Fuel (All Types) MSDS No. 9909
Revision Date: 10/18/2006 Page 7 of 7
16. OTHER INFORMATION NFPA® HAZARD RATING HEALTH: 0 FIRE: 2 REACTIVITY: 0 Refer to NFPA 704 “Identification of the Fire Hazards of Materials” for further information HMIS® HAZARD RATING HEALTH: 1 * * Chronic FIRE: 2 PHYSICAL: 0
SUPERSEDES MSDS DATED: 02/28/2001
ABBREVIATIONS: AP = Approximately < = Less than > = Greater than N/A = Not Applicable N/D = Not Determined ppm = parts per million
ACRONYMS: ACGIH American Conference of Governmental
Industrial Hygienists AIHA American Industrial Hygiene Association ANSI American National Standards Institute
(212) 642-4900 API American Petroleum Institute (202) 682-8000 CERCLA Comprehensive Emergency Response,
Compensation, and Liability Act DOT U.S. Department of Transportation
[General info: (800) 467-4922] EPA U.S. Environmental Protection Agency HMIS Hazardous Materials Information System IARC International Agency For Research On
Cancer MSHA Mine Safety and Health Administration NFPA National Fire Protection Association
(617)770-3000 NIOSH National Institute of Occupational Safety
and Health NOIC Notice of Intended Change (proposed
change to ACGIH TLV)
NTP National Toxicology Program OPA Oil Pollution Act of 1990 OSHA U.S. Occupational Safety & Health
Administration PEL Permissible Exposure Limit (OSHA) RCRA Resource Conservation and Recovery
Act REL Recommended Exposure Limit (NIOSH) SARA Superfund Amendments and
Reauthorization Act of 1986 Title III SCBA Self-Contained Breathing Apparatus SPCC Spill Prevention, Control, and
Countermeasures STEL Short-Term Exposure Limit (generally
15 minutes) TLV Threshold Limit Value (ACGIH) TSCA Toxic Substances Control Act TWA Time Weighted Average (8 hr.) WEEL Workplace Environmental Exposure
Level (AIHA) WHMIS Canadian Workplace Hazardous
Materials Information System DISCLAIMER OF EXPRESSED AND IMPLIED WARRANTIES Information presented herein has been compiled from sources considered to be dependable, and is accurate and reliable to the best of our knowledge and belief, but is not guaranteed to be so. Since conditions of use are beyond our control, we make no warranties, expressed or implied, except those that may be contained in our written contract of sale or acknowledgment.
Vendor assumes no responsibility for injury to vendee or third persons proximately caused by the material if reasonable safety procedures are not adhered to as stipulated in the data sheet. Additionally, vendor assumes no responsibility for injury to vendee or third persons proximately caused by abnormal use of the material, even if reasonable safety procedures are followed. Furthermore, vendee assumes the risk in their use of the material.
MATERIAL SAFETY DATA SHEET
Gasoline, All Grades MSDS No. 9950
Revision Date: 09/25/2007 Page 1 of 9
NFPA 704 (Section 16)
EMERGENCY OVERVIEW DANGER!
EXTREMELY FLAMMABLE - EYE AND MUCOUS MEMBRANE IRRITANT - EFFECTS CENTRAL NERVOUS SYSTEM - HARMFUL OR FATAL IF
SWALLOWED - ASPIRATION HAZARD High fire hazard. Keep away from heat, spark, open flame, and other ignition sources.
If ingested, do NOT induce vomiting, as this may cause chemical pneumonia (fluid in the lungs). Contact may cause eye, skin and mucous membrane irritation. Harmful if absorbed through the skin. Avoid prolonged breathing of vapors or mists. Inhalation may cause irritation, anesthetic effects (dizziness, nausea, headache, intoxication), and respiratory system effects.
Long-term exposure may cause effects to specific organs, such as to the liver, kidneys, blood, nervous system, and skin. Contains benzene, which can cause blood disease, including anemia and leukemia.
1. CHEMICAL PRODUCT and COMPANY INFORMATION
Hess Corporation 1 Hess Plaza Woodbridge, NJ 07095-0961
EMERGENCY TELEPHONE NUMBER (24 hrs): CHEMTREC (800)424-9300 COMPANY CONTACT (business hours): Corporate Safety (732)750-6000 MSDS (Environment, Health, Safety) Internet Website www.hess.com
SYNONYMS: Hess Conventional (Oxygenated and Non-oxygenated) Gasoline; Reformulated Gasoline (RFG); Reformulated Gasoline Blendstock for Oxygenate Blending (RBOB); Unleaded Motor or Automotive Gasoline
See Section 16 for abbreviations and acronyms.
2. COMPOSITION and INFORMATION ON INGREDIENTS *
INGREDIENT NAME (CAS No.) CONCENTRATION PERCENT BY WEIGHT Gasoline (86290-81-5) 100 Benzene (71-43-2) 0.1 - 4.9 (0.1 - 1.3 reformulated gasoline) n-Butane (106-97-8) < 10 Ethyl Alcohol (Ethanol) (64-17-5) 0 - 10 Ethyl benzene (100-41-4) < 3 n-Hexane (110-54-3) 0.5 to 4 Methyl-tertiary butyl ether (MTBE) (1634-04-4) 0 to 15.0 Tertiary-amyl methyl ether (TAME) (994-05-8) 0 to 17.2 Toluene (108-88-3) 1 - 25 1,2,4- Trimethylbenzene (95-63-6) < 6 Xylene, mixed isomers (1330-20-7) 1 - 15 A complex blend of petroleum-derived normal and branched-chain alkane, cycloalkane, alkene, and aromatic hydrocarbons. May contain antioxidant and multifunctional additives. Non-oxygenated Conventional Gasoline and RBOB do not have oxygenates (Ethanol or MTBE and/or TAME).
MATERIAL SAFETY DATA SHEET
Gasoline, All Grades MSDS No. 9950
Revision Date: 09/25/2007 Page 2 of 9
Oxygenated Conventional and Reformulated Gasoline will have oxygenates for octane enhancement or as legally required.
3. HAZARDS IDENTIFICATION
EYES Moderate irritant. Contact with liquid or vapor may cause irritation.
SKIN Practically non-toxic if absorbed following acute (single) exposure. May cause skin irritation with prolonged or repeated contact. Liquid may be absorbed through the skin in toxic amounts if large areas of skin are exposed repeatedly.
INGESTION The major health threat of ingestion occurs from the danger of aspiration (breathing) of liquid drops into the lungs, particularly from vomiting. Aspiration may result in chemical pneumonia (fluid in the lungs), severe lung damage, respiratory failure and even death.
Ingestion may cause gastrointestinal disturbances, including irritation, nausea, vomiting and diarrhea, and central nervous system (brain) effects similar to alcohol intoxication. In severe cases, tremors, convulsions, loss of consciousness, coma, respiratory arrest, and death may occur.
INHALATION Excessive exposure may cause irritations to the nose, throat, lungs and respiratory tract. Central nervous system (brain) effects may include headache, dizziness, loss of balance and coordination, unconsciousness, coma, respiratory failure, and death.
WARNING: the burning of any hydrocarbon as a fuel in an area without adequate ventilation may result in hazardous levels of combustion products, including carbon monoxide, and inadequate oxygen levels, which may cause unconsciousness, suffocation, and death.
CHRONIC EFFECTS and CARCINOGENICITY Contains benzene, a regulated human carcinogen. Benzene has the potential to cause anemia and other blood diseases, including leukemia, after repeated and prolonged exposure. Exposure to light hydrocarbons in the same boiling range as this product has been associated in animal studies with systemic toxicity. See also Section 11 - Toxicological Information.
MEDICAL CONDITIONS AGGRAVATED BY EXPOSURE Irritation from skin exposure may aggravate existing open wounds, skin disorders, and dermatitis (rash). Chronic respiratory disease, liver or kidney dysfunction, or pre-existing central nervous system disorders may be aggravated by exposure.
4. FIRST AID MEASURES EYES In case of contact with eyes, immediately flush with clean, low-pressure water for at least 15 min. Hold eyelids open to ensure adequate flushing. Seek medical attention.
SKIN Remove contaminated clothing. Wash contaminated areas thoroughly with soap and water or waterless hand cleanser. Obtain medical attention if irritation or redness develops.
INGESTION
MATERIAL SAFETY DATA SHEET
Gasoline, All Grades MSDS No. 9950
Revision Date: 09/25/2007 Page 3 of 9
DO NOT INDUCE VOMITING. Do not give liquids. Obtain immediate medical attention. If spontaneous vomiting occurs, lean victim forward to reduce the risk of aspiration. Small amounts of material which enter the mouth should be rinsed out until the taste is dissipated.
INHALATION Remove person to fresh air. If person is not breathing, ensure an open airway and provide artificial respiration. If necessary, provide additional oxygen once breathing is restored if trained to do so. Seek medical attention immediately.
5. FIRE FIGHTING MEASURES FLAMMABLE PROPERTIES: FLASH POINT: -45 oF (-43oC) AUTOIGNITION TEMPERATURE: highly variable; > 530 oF (>280 oC) OSHA/NFPA FLAMMABILITY CLASS: 1A (flammable liquid) LOWER EXPLOSIVE LIMIT (%): 1.4% UPPER EXPLOSIVE LIMIT (%): 7.6%
FIRE AND EXPLOSION HAZARDS Vapors may be ignited rapidly when exposed to heat, spark, open flame or other source of ignition. Flowing product may be ignited by self-generated static electricity. When mixed with air and exposed to an ignition source, flammable vapors can burn in the open or explode in confined spaces. Being heavier than air, vapors may travel long distances to an ignition source and flash back. Runoff to sewer may cause fire or explosion hazard.
EXTINGUISHING MEDIA SMALL FIRES: Any extinguisher suitable for Class B fires, dry chemical, CO2, water spray, fire fighting foam, or Halon.
LARGE FIRES: Water spray, fog or fire fighting foam. Water may be ineffective for fighting the fire, but may be used to cool fire-exposed containers.
During certain times of the year and/or in certain geographical locations, gasoline may contain MTBE and/or TAME. Firefighting foam suitable for polar solvents is recommended for fuel with greater than 10% oxygenate concentration - refer to NFPA 11 “Low Expansion Foam - 1994 Edition.”
FIRE FIGHTING INSTRUCTIONS Small fires in the incipient (beginning) stage may typically be extinguished using handheld portable fire extinguishers and other fire fighting equipment.
Firefighting activities that may result in potential exposure to high heat, smoke or toxic by-products of combustion should require NIOSH/MSHA- approved pressure-demand self-contained breathing apparatus with full facepiece and full protective clothing.
Isolate area around container involved in fire. Cool tanks, shells, and containers exposed to fire and excessive heat with water. For massive fires the use of unmanned hose holders or monitor nozzles may be advantageous to further minimize personnel exposure. Major fires may require withdrawal, allowing the tank to burn. Large storage tank fires typically require specially trained personnel and equipment to extinguish the fire, often including the need for properly applied fire fighting foam.
See Section 16 for the NFPA 704 Hazard Rating.
MATERIAL SAFETY DATA SHEET
Gasoline, All Grades MSDS No. 9950
Revision Date: 09/25/2007 Page 4 of 9
6. ACCIDENTAL RELEASE MEASURES ACTIVATE FACILITY SPILL CONTINGENCY or EMERGENCY PLAN.
Evacuate nonessential personnel and remove or secure all ignition sources. Consider wind direction; stay upwind and uphill, if possible. Evaluate the direction of product travel, diking, sewers, etc. to confirm spill areas. Spills may infiltrate subsurface soil and groundwater; professional assistance may be necessary to determine the extent of subsurface impact.
Carefully contain and stop the source of the spill, if safe to do so. Protect bodies of water by diking, absorbents, or absorbent boom, if possible. Do not flush down sewer or drainage systems, unless system is designed and permitted to handle such material. The use of fire fighting foam may be useful in certain situations to reduce vapors. The proper use of water spray may effectively disperse product vapors or the liquid itself, preventing contact with ignition sources or areas/equipment that require protection.
Take up with sand or other oil absorbing materials. Carefully shovel, scoop or sweep up into a waste container for reclamation or disposal - caution, flammable vapors may accumulate in closed containers. Response and clean-up crews must be properly trained and must utilize proper protective equipment (see Section 8).
7. HANDLING and STORAGE HANDLING PRECAUTIONS
******USE ONLY AS A MOTOR FUEL****** ******DO NOT SIPHON BY MOUTH******
Handle as a flammable liquid. Keep away from heat, sparks, and open flame! Electrical equipment should be approved for classified area. Bond and ground containers during product transfer to reduce the possibility of static-initiated fire or explosion.
Special slow load procedures for "switch loading" must be followed to avoid the static ignition hazard that can exist when higher flash point material (such as fuel oil) is loaded into tanks previously containing low flash point products (such as this product) - see API Publication 2003, "Protection Against Ignitions Arising Out Of Static, Lightning and Stray Currents.
STORAGE PRECAUTIONS Keep away from flame, sparks, excessive temperatures and open flame. Use approved vented containers. Keep containers closed and clearly labeled. Empty product containers or vessels may contain explosive vapors. Do not pressurize, cut, heat, weld or expose such containers to sources of ignition.
Store in a well-ventilated area. This storage area should comply with NFPA 30 "Flammable and Combustible Liquid Code". Avoid storage near incompatible materials. The cleaning of tanks previously containing this product should follow API Recommended Practice (RP) 2013 "Cleaning Mobile Tanks In Flammable and Combustible Liquid Service" and API RP 2015 "Cleaning Petroleum Storage Tanks".
WORK/HYGIENIC PRACTICES Emergency eye wash capability should be available in the near proximity to operations presenting a potential splash exposure. Use good personal hygiene practices. Avoid repeated and/or prolonged skin exposure. Wash hands before eating, drinking, smoking, or using toilet facilities. Do not use as a cleaning solvent on the skin. Do not use solvents or harsh abrasive skin cleaners for washing this product from exposed skin areas. Waterless hand cleaners are effective. Promptly remove contaminated clothing and launder before reuse. Use care when laundering to prevent the formation of flammable vapors which could ignite via washer or dryer. Consider the need to discard contaminated leather shoes and gloves.
MATERIAL SAFETY DATA SHEET
Gasoline, All Grades MSDS No. 9950
Revision Date: 09/25/2007 Page 5 of 9
8. EXPOSURE CONTROLS and PERSONAL PROTECTION EXPOSURE LIMITS
Component (CAS No.) Exposure Limits Source TWA
(ppm) STEL (ppm)
Note
Gasoline (86290-81-5) ACGIH 300 500 A3 Benzene (71-43-2) OSHA
ACGIH USCG
1 0.5 1
5 2.5 5
Carcinogen A1, skin
n-Butane (106-97-8) ACGIH 1000 -- Aliphatic Hydrocarbon Gases Alkane (C1-C4) Ethyl Alcohol (ethanol) (64-17-5) OSHA
ACGIH 1000 1000
-- --
A4
Ethyl benzene (100-41-4) OSHA ACGIH
100 100
-- 125
A3
n-Hexane (110-54-3) OSHA ACGIH
500 50
-- --
Skin
Methyl-tertiary butyl ether [MTBE] (1634-04-4) ACGIH 50 A3 Tertiary-amyl methyl ether [TAME] (994-05-8) None established Toluene (108-88-3) OSHA
ACGIH 200 20
--
Ceiling: 300 ppm; Peak: 500 ppm (10 min.) A4
1,2,4- Trimethylbenzene (95-63-6) ACGIH 25 -- Xylene, mixed isomers (1330-20-7) OSHA
ACGIH 100 100
-- 150
A4
ENGINEERING CONTROLS Use adequate ventilation to keep vapor concentrations of this product below occupational exposure and flammability limits, particularly in confined spaces.
EYE/FACE PROTECTION Safety glasses or goggles are recommended where there is a possibility of splashing or spraying.
SKIN PROTECTION Gloves constructed of nitrile or neoprene are recommended. Chemical protective clothing such as that made of of E.I. DuPont Tychem ®, products or equivalent is recommended based on degree of exposure.
Note: The resistance of specific material may vary from product to product as well as with degree of exposure. Consult manufacturer specifications for further information.
RESPIRATORY PROTECTION A NIOSH-approved air-purifying respirator with organic vapor cartridges or canister may be permissible under certain circumstances where airborne concentrations are or may be expected to exceed exposure limits or for odor or irritation. Protection provided by air-purifying respirators is limited. Refer to OSHA 29 CFR 1910.134, NIOSH Respirator Decision Logic, and the manufacturer for additional guidance on respiratory protection selection and limitations.
Use a positive pressure, air-supplied respirator if there is a potential for uncontrolled release, exposure levels are not known, in oxygen-deficient atmospheres, or any other circumstance where an air-purifying respirator may not provide adequate protection.
9. PHYSICAL and CHEMICAL PROPERTIES APPEARANCE A translucent, straw-colored or light yellow liquid
MATERIAL SAFETY DATA SHEET
Gasoline, All Grades MSDS No. 9950
Revision Date: 09/25/2007 Page 6 of 9
ODOR A strong, characteristic aromatic hydrocarbon odor. Oxygenated gasoline with MTBE and/or TAME may have a sweet, ether-like odor and is detectable at a lower concentration than non-oxygenated gasoline.
ODOR THRESHOLD Odor Detection Odor Recognition Non-oxygenated gasoline: 0.5 - 0.6 ppm 0.8 - 1.1 ppm Gasoline with 15% MTBE: 0.2 - 0.3 ppm 0.4 - 0.7 ppm Gasoline with 15% TAME: 0.1 ppm 0.2 ppm
BASIC PHYSICAL PROPERTIES BOILING RANGE: 85 to 437 oF (39 to 200 oC) VAPOR PRESSURE: 6.4 - 15 RVP @ 100 oF (38 oC) (275-475 mm Hg @ 68 oF (20 oC) VAPOR DENSITY (air = 1): AP 3 to 4 SPECIFIC GRAVITY (H2O = 1): 0.70 – 0.78 EVAPORATION RATE: 10-11 (n-butyl acetate = 1) PERCENT VOLATILES: 100 % SOLUBILITY (H2O): Non-oxygenated gasoline - negligible (< 0.1% @ 77 oF). Gasoline with 15%
MTBE - slight (0.1 - 3% @ 77 oF); ethanol is readily soluble in water
10. STABILITY and REACTIVITY ) STABILITY: Stable. Hazardous polymerization will not occur.
CONDITIONS TO AVOID Avoid high temperatures, open flames, sparks, welding, smoking and other ignition sources
INCOMPATIBLE MATERIALS Keep away from strong oxidizers.
HAZARDOUS DECOMPOSITION PRODUCTS Carbon monoxide, carbon dioxide and non-combusted hydrocarbons (smoke). Contact with nitric and sulfuric acids will form nitrocresols that can decompose violently.
11. TOXICOLOGICAL PROPERTIES ACUTE TOXICITY Acute Dermal LD50 (rabbits): > 5 ml/kg Acute Oral LD50 (rat): 18.75 ml/kg Primary dermal irritation (rabbits): slightly irritating Draize eye irritation (rabbits): non-irritating Guinea pig sensitization: negative
CHRONIC EFFECTS AND CARCINOGENICITY Carcinogenicity: OSHA: NO IARC: YES - 2B NTP: NO ACGIH: YES (A3)
IARC has determined that gasoline and gasoline exhaust are possibly carcinogenic in humans. Inhalation exposure to completely vaporized unleaded gasoline caused kidney cancers in male rats and liver tumors in female mice. The U.S. EPA has determined that the male kidney tumors are species-specific and are irrelevant for human health risk assessment. The significance of the tumors seen in female mice is not known. Exposure to light hydrocarbons in the same boiling range as this product has been associated in animal studies with effects to the central and peripheral nervous systems, liver, and kidneys. The significance of these animal models to predict similar human response to gasoline is uncertain.
This product contains benzene. Human health studies indicate that prolonged and/or repeated overexposure to benzene may cause damage to the blood-forming system (particularly bone marrow), and serious blood disorders such as aplastic anemia and leukemia. Benzene is listed as a human carcinogen by the NTP, IARC, OSHA and ACGIH.
MATERIAL SAFETY DATA SHEET
Gasoline, All Grades MSDS No. 9950
Revision Date: 09/25/2007 Page 7 of 9
This product may contain methyl tertiary butyl ether (MTBE ): animal and human health effects studies indicate that MTBE may cause eye, skin, and respiratory tract irritation, central nervous system depression and neurotoxicity. MTBE is classified as an animal carcinogen (A3) by the ACGIH.
12. ECOLOGICAL INFORMATION Keep out of sewers, drainage areas and waterways. Report spills and releases, as applicable, under Federal and State regulations. If released, oxygenates such as ethers and alcohols will be expected to exhibit fairly high mobility in soil, and therefore may leach into groundwater. The API (www.api.org) provides a number of useful references addressing petroleum and oxygenate contamination of groundwater.
13. DISPOSAL CONSIDERATIONS Consult federal, state and local waste regulations to determine appropriate disposal options.
14. TRANSPORTATION INFORMATION DOT PROPER SHIPPING NAME: Gasoline DOT HAZARD CLASS and PACKING GROUP: 3, PG II DOT IDENTIFICATION NUMBER: UN 1203 DOT SHIPPING LABEL:
FLAMMABLE LIQUID
PLACARD:
15. REGULATORY INFORMATION U.S. FEDERAL, STATE, and LOCAL REGULATORY INFORMATION This product and its constituents listed herein are on the EPA TSCA Inventory. Any spill or uncontrolled release of this product, including any substantial threat of release, may be subject to federal, state and/or local reporting requirements. This product and/or its constituents may also be subject to other federal, state, or local regulations; consult those regulations applicable to your facility/operation.
CLEAN WATER ACT (OIL SPILLS) Any spill or release of this product to "navigable waters" (essentially any surface water, including certain wetlands) or adjoining shorelines sufficient to cause a visible sheen or deposit of a sludge or emulsion must be reported immediately to the National Response Center (1-800-424-8802) as required by U.S. Federal Law. Also contact appropriate state and local regulatory agencies as required.
CERCLA SECTION 103 and SARA SECTION 304 (RELEASE TO THE ENVIRONMENT) The CERCLA definition of hazardous substances contains a “petroleum exclusion” clause which exempts crude oil, refined, and unrefined petroleum products and any indigenous components of such. However, other federal reporting requirements (e.g., SARA Section 304 as well as the Clean Water Act if the spill occurs on navigable waters) may still apply.
SARA SECTION 311/312 - HAZARD CLASSES ACUTE HEALTH CHRONIC HEALTH FIRE SUDDEN RELEASE OF PRESSURE REACTIVE
X X X -- --
SARA SECTION 313 - SUPPLIER NOTIFICATION This product contains the following toxic chemicals subject to the reporting requirements of section 313 of the Emergency Planning and Community Right-To-Know Act (EPCRA) of 1986 and of 40 CFR 372:
INGREDIENT NAME (CAS NUMBER) CONCENTRATION WT. PERCENT Benzene (71-43-2) 0.1 to 4.9 (0.1 to 1.3 for reformulated gasoline)
Ethyl benzene (100-41-4) < 3
MATERIAL SAFETY DATA SHEET
Gasoline, All Grades MSDS No. 9950
Revision Date: 09/25/2007 Page 8 of 9
n-Hexane (110-54-3) 0.5 to 4
Methyl-tertiary butyl ether (MTBE) (1634-04-4) 0 to 15.0
Toluene (108-88-3) 1 to 15
1,2,4- Trimethylbenzene (95-63-6) < 6
Xylene, mixed isomers (1330-20-7) 1 to 15
US EPA guidance documents (www.epa.gov/tri) for reporting Persistent Bioaccumulating Toxics (PBTs) indicate this product may contain the following deminimis levels of toxic chemicals subject to Section 313 reporting:
INGREDIENT NAME (CAS NUMBER) CONCENTRATION - Parts per million (ppm) by weight Polycyclic aromatic compounds (PACs) Benzo (g,h,i) perylene (191-24-2) Lead (7439-92-1)
17 2.55 0.079
CALIFORNIA PROPOSITION 65 LIST OF CHEMICALS This product contains the following chemicals that are included on the Proposition 65 “List of Chemicals” required by the California Safe Drinking Water and Toxic Enforcement Act of 1986:
INGREDIENT NAME (CAS NUMBER) Date Listed Benzene 2/27/1987 Ethyl benzene 6/11/2004 Toluene 1/1/1991 CANADIAN REGULATORY INFORMATION (WHMIS) Class B, Division 2 (Flammable Liquid) Class D, Division 2A (Very toxic by other means) and Class D, Division 2B (Toxic by other means)
16. OTHER INFORMATION NFPA® HAZARD RATING HEALTH: 1 Slight FIRE: 3 Serious REACTIVITY: 0 Minimal
HMIS® HAZARD RATING HEALTH: 1 * Slight FIRE: 3 Serious PHYSICAL: 0 Minimal * CHRONIC
SUPERSEDES MSDS DATED: 07/01/06
ABBREVIATIONS: AP = Approximately < = Less than > = Greater than N/A = Not Applicable N/D = Not Determined ppm = parts per million
ACRONYMS: ACGIH American Conference of Governmental
Industrial Hygienists AIHA American Industrial Hygiene Association ANSI American National Standards Institute
(212)642-4900 API American Petroleum Institute
(202)682-8000
CERCLA Comprehensive Emergency Response, Compensation, and Liability Act
DOT U.S. Department of Transportation [General Info: (800)467-4922]
EPA U.S. Environmental Protection Agency HMIS Hazardous Materials Information System
MATERIAL SAFETY DATA SHEET
Gasoline, All Grades MSDS No. 9950
Revision Date: 09/25/2007 Page 9 of 9
IARC International Agency For Research On Cancer
MSHA Mine Safety and Health Administration NFPA National Fire Protection Association
(617)770-3000 NIOSH National Institute of Occupational Safety
and Health NOIC Notice of Intended Change (proposed
change to ACGIH TLV) NTP National Toxicology Program OPA Oil Pollution Act of 1990 OSHA U.S. Occupational Safety & Health
Administration PEL Permissible Exposure Limit (OSHA) RCRA Resource Conservation and Recovery Act
REL Recommended Exposure Limit (NIOSH) SARA Superfund Amendments and
Reauthorization Act of 1986 Title III SCBA Self-Contained Breathing Apparatus SPCC Spill Prevention, Control, and
Countermeasures STEL Short-Term Exposure Limit (generally 15
minutes) TLV Threshold Limit Value (ACGIH) TSCA Toxic Substances Control Act TWA Time Weighted Average (8 hr.) WEEL Workplace Environmental Exposure
Level (AIHA) WHMIS Workplace Hazardous Materials
Information System (Canada)
DISCLAIMER OF EXPRESSED AND IMPLIED WARRANTIES
Information presented herein has been compiled from sources considered to be dependable, and is accurate and reliable to the best of our knowledge and belief, but is not guaranteed to be so. Since conditions of use are beyond our control, we make no warranties, expressed or implied, except those that may be contained in our written contract of sale or acknowledgment.
Vendor assumes no responsibility for injury to vendee or third persons proximately caused by the material if reasonable safety procedures are not adhered to as stipulated in the data sheet. Additionally, vendor assumes no responsibility for injury to vendee or third persons proximately caused by abnormal use of the material, even if reasonable safety procedures are followed. Furthermore, vendee assumes the risk in their use of the material.
Material Safety Data Sheet
SECTION I - Material Identity SECTION II - Manufacturer's Information SECTION III - Physical/Chemical Characteristics SECTION IV - Fire and Explosion Hazard Data SECTION V - Reactivity Data SECTION VI - Health Hazard Data SECTION VII - Precautions for Safe Handling and Use SECTION VIII - Control Measures SECTION IX - Label Data SECTION X - Transportation Data SECTION XI - Site Specific/Reporting Information SECTION XII - Ingredients/Identity Information
SECTION I - Material Identity
SECTION II - Manufacturer's Information
MSDS Preparer's Information
Item Name
Part Number/Trade Name LUBRIPLATE HYDRAULIC OIL, SPECIAL LOW (SUPP
National Stock Number 9150L400652F
CAGE Code 73219
Part Number Indicator A
MSDS Number 184027
HAZ Code B
Manufacturer Name FISKE BROTHERS REFINING CO
Street 129 LOCKWOOD ST
City NEWARK
State NJ
Country US
Zip Code 07105
Emergency Phone 201-589-9150
Information Phone 201-589-9150
MSDS Preparer Name ROBERT J. SIBILIA
Date MSDS Prepared/Revised 01JUL90
Date of Technical Review 10SEP92
Active Indicator N
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Alternate Vendors
SECTION III - Physical/Chemical Characteristics
SECTION IV - Fire and Explosion Hazard Data
SECTION V - Reactivity Data
Vendor #5 CAGE BPXSL
Hazard Storage Compatibility Code N1
Appearance/Odor TRANSPARENT AMBER OIL WITH MINERAL OIL ODOR
Boiling Point >550F,>288C
Melting Point LIQUID
Vapor Pressure <0.01
Vapor Density >5
Specific Gravity 0.87
Decomposition Temperature N/K
Evaporation Rate <0.01 (BUTYL ACETATE=1)
Solubility in Water NEGLIGIBLE
Percent Volatiles by Volume N/K
Chemical pH N/K
Corrosion Rate N/K
Container Pressure Code 4
Temperature Code 8
Product State Code U
Flash Point 315
Flash Point Method COC
Lower Explosion Limit 0.9%
Upper Explosion Limit 7%
Extinguishing Media FOAM, DRY CHEMICAL, CARBON DIOXIDE OR WATER
SPRAY(FOG)
Special Fire Fighting Procedures WEAR NIOSH/MSHA APPROVED SCBA AND FULL
PROTECTIVEEQUIPMENT (FP N). COOL EXPOSED
CONTAINERS WITH WATER
Unusual Fire/Explosion Hazards DO NOT STORE OR MIX WITH STRONG OXIDANTS.
EMPTY CONTAINERS RETAIN RESIDUE. DO NOT CUT,
DRILL, GRIND OR WELD AS THEY MAYEXPLODE
Stability YES
Stability Conditions to Avoid NOT APPLICABLE
Materials to Avoid AVOID CONTACT WITH STRONG OXIDANTS LIKE
LIQUID CHLORINE, CONCENTRATED OXYGEN
Hazardous Decomposition Products MAY FORM SO*2. IF INCOMPLETE COMBUSTION,
CARBON MONOXIDE
Hazardous Polymerization NO
Polymerization Conditions to Avoid NOT RELEVANT
LD50 - LD50 Mixture NONE SPECIFIED BY MANUFACTURER
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SECTION VI - Health Hazard Data
SECTION VII - Precautions for Safe Handling and Use
SECTION VIII - Control Measures
Route of Entry: Skin NO
Route of Entry: Ingestion YES
Route of Entry: Inhalation YES
Health Hazards - Acute and Chronic PRLNGD/RPTD SKIN CONT MAY CAUSE IRRIT.PRDCT
CONTACTING EYES MAY CAUSE IRRIT. HUMAN HLTH
RISKS VARY FROM PERS TO PERS. AS A PREC,
EXPOS TO LIQS, VAPS, MISTS & FUMES SHLD BE
MINIMIZED. PROD HAS LOW ORDER OF ACUTE ORAL
TOX, BUT MINUTE AMTS ASPIRATED INTO LUNGS
DURING INGEST MAY CAUSE MILD TO SEVERE
PULMONARY INJURY
Carcinogenity: NTP NO
Carcinogenity: IARC NO
Carcinogenity: OSHA NO
Explanation of Carcinogenity NOT RELEVANT
Symptoms of Overexposure SEE HEALTH HAZARDS
Medical Cond. Aggrevated by Exposure NONE SPECIFIED BY MANUFACTURER
Emergency/First Aid Procedures EYE:FLUSH W/CLEAR WATER FOR @ LST 15
MIN/UNTIL IRRIT SUBSIDES.IF IRRIT PERSISTS,
CONSULT MD. SKIN:REMOVE ANY CONTAMD CLTHG
&WASH THORO W/SOAP & WARM WATER. INHAL:VAP
PRESS IS VERY LOW & INHAL @ ROOMTEMP IS NOT
A PROBLEM.IF OVERCOME BY VAP FROM HOT PROD,
IMMED MOVE FROM EXPOS & CALL MD. IF
OVEREXPOS TO OIL MIST, REMOVE FROM FURTHER
EXPOS UNTIL EXCESSIVE OIL MIST CONDITION
SUBSIDES. (SUPP DATA)
Steps if Material Released/Spilled RECOVER LIQUID, WASH REMAINDER WITH SUITABLE
PETROLEUM SOLVENT OR ADD ABSORBENT. KEEP
PETROLEUM PRODUCTS OUT OF SEWERS AND WATER
COURSES. ADVISE AUTHORITIES IF PRODUCT HAS
ENTERED OR MAY ENTER SEWERS AND
WATERCOURSES
Neutralizing Agent NONE SPECIFIED BY MANUFACTURER
Waste Disposal Method ASSURE CONFORMITY WITH APPLICABLE DISPOSAL
REGULATIONS. DISPOSE OF ABSORBED MATERIAL AT
AN APPROVED WASTE DISPOSAL FACILITY OR SITE.
DISPOSE I/A/W FEDERAL, STATE AND LOCAL
REGULATIONS (FP N)
Handling and Storage Precautions KEEP CONTAINERS CLOSED WHEN NOT IN USE. DO
NOT HANDLE OR STORE NEAR HEAT, SPARKS, FLAME
OR STRONG OXIDANTS
Other Precautions AVOID BREATHING OIL MIST. REMOVE OIL-SOAKED
CLOTHING AND LAUNDER BEFORE RESUE
Respiratory Protection NORMALLY NOT NEEDED. NIOSH/MSHA APPROVED
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SECTION IX - Label Data
SECTION X - Transportation Data
SECTION XI - Site Specific/Reporting Information
SECTION XII - Ingredients/Identity Information
RESPIRATOR APPROPRIATE FOR EXPOSURE OF
CONCERN (FP N)
Ventilation LOCAL EXHAUST: USED TO CAPTURE FUMES AND
VAPORS
Protective Gloves USE OIL-RESISTANT GLOVES, IF NEEDED
Eye Protection CHEMICAL WORKERS GOGGLES (FP N)
Other Protective Equipment USE OIL-RESISTANT APRON, IF NEEDED
Work Hygenic Practices CLEANSE SKIN THOROUGHLY AFTER CONTACT
Supplemental Health/Safety Data MFR'S TRADE NAME/PART NO: POUR, MINUS 70,
MV-HO. FIRST AID PROC: INGEST: IF INGESTED,
CALL MD IMMEDIATELY. DO NOT INDUCE VOMITING
Protect Eye NO
Protect Skin NO
Protect Respiratory NO
Chronic Indicator UNKNOWN
Contact Code UNKNOWN
Fire Code UNKNOWN
Health Code UNKNOWN
React Code UNKNOWN
Container Quantity 1
Unit of Measure GL
Volatile Organic Compounds (P/G) 0
Volatile Organic Compounds (G/L) 0
Ingredient # 01
Ingredient Name OIL, HYDRAULIC (MIST); (OIL MIST)
CAS Number 1003
NIOSH Number 1005034OH
Proprietary NO
Percent 0
OSHA PEL 5 MG/M3
ACGIH TLV 5 MG/M3;10 STEL
Recommended Limit N/K
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LANGAN EHS PLAN FIELD CHANGE AUTHORIZATION REQUEST FORM
PROJECT: _______________________________________________________________________
PROJECT LOCATION:_____________________________________________________________
DESCRIPTION OF CHANGE:
REASON FOR CHANGE:
RECOMMENDED DISPOSITION:
APPROVALS
PROJECT MANAGER:
Signature Date
PROJECT SITE SAFETY OFFICER:
Signature Date
CLIENT REPRESENTATIVE:
Signature Date
DISTRIBUTION: Langan SSO
Langan Site Supervisor
Langan Project Manager
Client Project Manager
FIELD CHANGE RECORDS
Record of Field Changes:
Initial for attaching any Field changes to this EHS Plan. Enter the Field Change Number and
Date Issued. File the completed field changes to this EHS Plan at the end as attachments.
Make PEN and INK changes in the text to alert the reader to the changes that are required in
the Field Change.
FIELD CHANGE
NUMBER
DATE ENTERED SYNOPSIS OF CHANGE INITIAL
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Authorization Forms.doc
LANGAN ACCIDENT/INCIDENT REPORT FORM
Page 1 of 2
Project Name:
Injured or Ill Employee
1. Name Social Security #
(First) (Middle) (Last)
2. Home Address
(No. and Street) (City or Town) (State, Zip)
3. Age _____
4. Sex: Male ( ) Female ( )
5. Occupation
(Specific job title, not the specific activity employee was performing at time of injury)
6. Department
(Enter name of department in which injured person is employed, even though they
may have been temporarily working in another department at the time of injury)
Employer
7. Name
8. Mailing Address
(No. and Street) (City or Town) (State, Zip)
9. Location (if different from mailing address):
THE ACCIDENT OR EXPOSURE TO OCCUPATIONAL ILLNESS
10. Place of accident or exposure
(No. and Street) (City or Town) (State, Zip)
11. Was place of accident or exposure on employer's premises? (Yes / No)
12. What was the employee doing when injured?
(Be specific ? was employee using tools or equipment or handling material?)
13. How did the accident occur?
(Describe fully the events that resulted in the injury or
occupational illness. Tell what happened and how. Name objects and substances involved.
Give details on all factors that led to accident. Use separate sheet if needed)
LANGAN ACCIDENT/INCIDENT REPORT FORM
Page 2 of 2
14. Time of accident: ________________
15. Date of injury or initial diagnosis of occupational illness _____________________________
(Date)
16. WITNESS
TO ACCIDENT (Name) (Affiliation) (Phone No.)
(Name) (Affiliation) (Phone No.)
(Name) (Affiliation) (Phone No.)
Occupational Injury/Illness
17. Describe the injury or illness in detail; indicate part of body affected.
18. Name the object or substance that directly injured the employee. (For example, object that struck
employee; the vapor or poison inhaled or swallowed; the chemical or radiation that irritated the
skin; or in cases of strains, hernias, etc., the object the employee was lifting, pulling, etc.)
19. Did the accident result in employee fatality? ________ (Yes or No)
20. Number of lost workdays ____/restricted workdays _____ resulting from injury
or illness?
Other
21. Did you see a physician for treatment? ________ (Yes or No) ________ (Date)
22. Name and address of physician
(No. and Street) (City or Town) (State and Zip)
23. If hospitalized, name and address of hospital
(No. and Street) (City or Town) (State and Zip)
Date of report ___________________ Prepared by
Official position ___________________________
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Accident Report Form.doc
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EMERGENCY CONTACTS\HASP-EMERGENCY CONTACTS.DOC
ATTACHMENT D
EMERGENCY NOTIFICATION NUMBERS
The following list provides names and telephone numbers for emergency contact personnel.
ORGANIZATION
CONTACT
TELEPHONE
New York City Police 911
New York City Fire 911
New York Downtown Hospital 212-348-2210
Langan Project Managers Chris McMahon
Steven Ciambruschini
201-794-6900 /
201-218-2339
201-398-4549 /
201-410-9238
National Response Center 800-424-8802
Center for Disease Control 404-488-4100
CHEMTREC 800-424-9300
TSCA HOTLINE 202-554-1404
RCRA HOTLINE 800-424-9346
CDC (DAY)
(NIGHT)
404-452-4100
404-329-2888
BUREAU OF ALCOHOL, TOBACCO & FIREARMS 800-424-9555
202-566-7777
NATIONAL RESPONSE CENTER 800-424-8802
PESTICIDE INFORMATION SERVICE 800-424-9346
BUREAU OF EXPLOSIVES, A.A. RAILWAYS 202-835-9500
FEDERAL EXPRESS - HAZARDOUS MATERIAL INFO 901-922-1666