background report reference section number: background ...€¦ · report number 9-658 november 28,...
TRANSCRIPT
Background Report Reference
AP-42 Section Number: 11.23
Background Chapter: 4
Reference Number: 40
Title:
-... .
Results of the October 23 and 24, 1979 Particulate Emission Compliance Tests on the Coarse Crusher Discharge, Crusher Dump Pocket Discharge and North Loading Tunnel at the Eveleth Taconite Company Thunderbird Mine
Interpoll, Inc.
Interpoll, Inc.
November 1979
Report Number 9-658 November 28, 1979
I n t e r p o l 1 Inc. 1996 West County Road C
St. Paul, Minnesota 55113
(612) 636-6866
AP42 Seftion 11.23 I Reference __
Report Sect. 4 I
Reference - i RESULTS OF THE OCTOBER 23 AND 24, 1979
PARTICULATE EMISSION COMPLIANCE TESTS ON THE COARSE CRUSHER DISCHARGE, CRUSHER
DUMP POCKET DISCHARGE AND NORTH LOADING TUNNEL AT THE EVELETH TACONITE COMPANY
THUNDERB I RD MI NE
Submitted t o :
EVELETH TACONITE COMPANY P. 0. Box 180
Eveleth, Minnesota 55734
A t t e n t i o n : D. S. Coyle Ch ie f M e t a i l u r g i s t
Approved by:
h
Perry . P i Lon s , ;zad,,, Ph.D.
D i r e c t o r bf Environmental Measurements Sect ion
I n t e r p o l l Inc. 1996 West County Road C
S t . Paul, Minnesota 55113
(612) 636-6866
RESULTS OF THE OCTOBER 23 AND 24, 1979 PARTICULATE EMISSION COMPLiANCE TESTS
ON THE COARSE CRUSHER DISCHARGE, CRUSHER DUMP POCKET DISCHARGE AND NORTH LOADING TUNNEL AT THE EVELETH TACONITE COMPANY
THUNDERBIRD MINE
Submitted t o :
EVELETH TACONITE COMPANY P. 0. Box 180
Eveleth, Minnesota 55734
A t t e n t i o n : D. S . Coyle Chief M e t a l l u r g i s t
Approved by:
n
Report Number 9-658 November 2 8 , 1979
Perry .w* Lon s . L Ph.D.
D i r e c t o r bf Environmental Measurements Sect ion
TABLE OF CONTENTS
SYMBOLS AND ABBREVIATIONS
I INTRODUCTION
2 SUMMARY AND DISCUSSION
3 RESULTS
3.1 Resul ts of Gas Analyses
3.1.1 Test No. 1 Coarse Crusher Discharge 3.1.2 Test No. 2 Crusher Dump Pocket Discharge 3.1.3 - T e s t No. 3 Nor th Loading Tunnel
3.2 Resul ts of P a r t i c l e Concentrat ion Determinat ions
3.2.1 Test No. 1 Coarse Crusher Discharge 3.2.2 Test No. 2 Crusher Dump Pocket Discharge 3.2.3 Test No. 3 North Loading Tunnel
3.3 Resul ts of Opaci ty Determinat ions
3.3.1 Test No. 1 Coarse Crusher Discharge 3.3.2 Test No. 2 Coarse Crusher Dump Pocket 3.3.3 Test No. 3 North Loading Tunnel
APPE?!D I CES :
A - Resul ts of Pre l lm lnary Measurements
B - Locat ion of Test Por ts and Traverse P o i n t s
C - Method 5 F i e l d Data Sheets
D - Method 9 F i e l d Data Sheets
E - Process Rate Log
F - Procedures
G - Calcu la t ion Equations
H - Sarnpllng T r a i n C a l i b r a t i o n Data Sheets
!
i i i
1
2
6
a 9 IO
12 13 14
16 17 18
t !
!
1 INTRODUCTION
On October 23 and 24 , 1979, I n t e r p o l I Inc. personnel conducted a
ag- ser ies of p a r t i c u l a t e emission Compliance t e s t s on t h e Coarse Crusher
house Discharge, the Crusher Dump Pocket Raghouse Discharge and the Nor th
Loading Baghouse Discharge a t t h e Eveleth Taconi te Company - Thunderbird
Mine. On-si te t e s t i n g was performed by E. Trowbridge and 0. VanHoever.
Coord inat ion between p l a n t opera t ion and t e s t i n g a c t i v i t i e s was provided
by D. J a r v i s o f Eveleth Taconi te Company. The t e s t s were no t witnessed
by a member o f t h e Minnesota P o l l u t i o n Contro l Agency.
P a r t i c u l a t e determinat ions were performed i n accordance w i t h EPA
Methods 1-5, CFR T i t l e 40, P a r t 60, Appendix A and t h e r e v i s i o n s to these
methods, FR g ( 1 0 0 ) . Pre l im inary determinat ions o f t h e gas l i n e a r v e l o c i t y
p r o f i l e were made on each o f t h e t h r e e sources before t h e s t a r t of t h e f i r s t
p a r t i c u l a t e determinat ion t o a l low s e l e c t i o n of t h e appropr ia te nozzle d ia -
meter requ i red f o r i s o k i n e t i c sample wi thdrawal. I n t e r p o l l sampling t r a i n s
which meet or exceed s p e c i f i c a t i o n s i n t h e above-cited references were used
t o i s o k l n e t l c a l i y e x t r a c t p a r t l c u l a t e samples by means of a heated s ta in less-
s t e e l l i n e d probe.
Tes t ing on each of t h e t h r e e sources was conducted from e x i s t i n g
t e s t p o r t s located on t h e duct leading t o t h e blower. Test ing pro toco l on
each source was based upon EPA Method 1 s p e c i f i c a t i o n s . A v i s i b l e emission
determinat ion was a l s o performed on each source by a c e r t i f i e d observer.
The important r e s u l t s of t h e t e s t a r e sumnarized i n Sect ion 2. De- t a i l e d r e s u l t s a r e presented i n Sect ion 3. Resul ts of p r e l i m i n a r y measure-
ments, f i e l d data and a l l o t h e r suppor t ing in format ion a r e presented i n t h e
appendices.
i
SYMBOLS AND ABBREVIATIONS
ACFM
DSCFM
D E G F
FT/SEC
GR/ACF
GR/DSCF
9 HRS
IN.
IN. H.G.
IN. W.C. LB
LB/HR
LB/ I O'BTU
mlcrons (pm) MIN
SO. FT.
V/ v
rng/DSCM
LB/DSCF
WH
ohmcm
HP
PS I w/w
ac tua l cub lc f e e t per minute
standard cubic f o o t of dry gas per minute
degrees Fahrenhei t
f e e t per second
g r a i n s p e r actua l cubic f o o t
g ra ins p e r dry standard cub ic f o o t
gram
hours
1 nches
inches of mercury
Inches o f water
pound
pounds per hour
m i i l l o n B r l t l s h Thermal U n i t s heat inpu t
m I cromotor
minutes
square f e e t
percent by volume
m l l l l g r a m s per dry standard cub ic meter
pounds p e r dry standard cub ic f o o t
megawatt hours
ohmcent imeter
horsepower
pounds per square Inch
percent by welght
Standard cond l t l ons a r e def lned as 68 OF (20 OC) and 29.92 In . o f mercury pressure.
1 1 1
!
i
i
n
C 0 t VI w a c c
n z 2
N
z a
-I W LT 0
B I- -
o\ Ln 00 . u nor- 0 r-r- 0 p’ r- o 00 o M o m 0 00 . r.
00 u . I r - n m L n . . . . n - N I I O 0. 0 - a
M N c o m e . 0 -- Nr- - -
cn Ln 00 . u nor- 0 r.p’ 0 m P u 00 0 rn o m 0 00 . p’
N N 0 . . . . 00 u . - 00, -- Nr- * . o - I L n 2 7 M N ..
I L A O L n - N l -
o, o 00 . u n o - o ‘ ~ m I- n P d 00 0 M o m 0 00 . a3 I n - N n . . . . 00 ID . PI - M N - 0 0 1 N I -- Nr- I O O M
- . o -
cno 00 . u r - 0 o o o y - I o , P I D 0 P? 0 NlN N -- I 0 -
t VI W t
0 W t
+-
m n
- u) LL I
t VI W t
0
- +-
E .- I-
-
0 >
u I
2
f!
n 1
a m
n
t L 0
El t VI
a m
> z \ > b4
t C W t
Y
E a L 3 t VI
0 E VI
a
.-
m
L U . > \ >
t u .-
.. LL u I \ Q, m + i - i
rn - W 3
z +
C 0
+
bQ
C
- 0 t m L m > U
t
.-
.-
.- 2 s1 .- Y
-
W t L m
5
El
.- VI VI .- a t
3 u t L
m - - 2
3
. . .
2 SUMMARY AND DISCUSSION
The impor tant r e s u l t s Of t he p a r t i c u l a t e emission compliance t e s t
As w i l l be noted, the measured p a r t i - are summarized i n Tables 1 , 2 and 3 .
c u l a t e concentrat ions ranged from .004 t o .a08 GR/DSCF.
No d i f f i c u l t i e s were encountered i n the f i e l d o r i n the labora tory
eva lua t ion of the samples. On the bas i s o f t h i s f a c t and a complete review
of t h e e n t i r e data and r e s u l t s , i t i s ou r op in ion t h a t t h e p a r t i c u l a t e con-
cen t ra t i ons and emission r a t e s repor ted he re in a re accurate and c lose ly re-
f l e c t t h e ac tua l values which ex i s ted a t t h e t ime the t e s t s were performed.
,
' $ 1 1 a
m r t
5 t m m k
m c c m a- - s u a
- i; c e 2 : m a L n c - + E W L
m > t c - 0 a E 0 0 - - u
m m
t m m c
m o m a f -u
- I - .L
u t
L w m > n w 0
t a r
N:
8 5 w t t
Y L U o m t
m v ) t
a 0 m c m c (La + m x u t c L V
0 >-J L
r m
--
- o m
E a 0 m z
wi
n 2 m -
- n
4 (L
m 0 00 . w MOP- 0 u u u 0 fi N 00 o w o m 0 00 . g
00 0 . 1 - m N U . . . . . o - 0 - w m 0 0 1
N I m n NP- I W 0 - - w
- -
m N 00 . w -01'. o u u o w P - 00 o 00 o m 0 - c o p . o m
00 * N I N - M u . . . . 00 N * . . o - - m m N P
m m 0 0 . co m o r - o n m m m P u 00 0 00 o m 0 0 0
u 0 W P 0 0 1 N I m m NI'.
I r n u w u . . . . 00 d -. . . a - -
t m 0 t
0 m t D
L
a
V m t c > ) . m
i v
c x 0 0 t u m c c m o o w o an c n ~ E L >t o m x - u u o c
- .- : .-
m t L. m
s
s .- m m .-
m t m a - U
t L
.- m a
5
- M
Z 3 (II
m u-t 00 r- -01- 0 m m n Q b - m 00 ~n o o m 0 00 . Ln I n cfm cf . . . . 00 M . o m * ' O N e - m m - N. - I M M Nr- - I O o n - N -
m o r - 0
I - *.- N I I n o m 0
- m
00 . r- o o Ln 0 Q U cf . m w - M w l
M o r - o m 0 o m
. . . RIP.
0 cfu m m 00 . M 00 M . . . a - -
m v\ 00 . m n o - o nln - o r- M 00 o N o m 0 00 . I-
00 9 - i m m m m . . . . . . o w n - m m - o m N l M M NP. i m
-
m L n 00 . c f
N
r - v \ 0 0 0 - I W L n r - L n . M - - m - o n
3 RESULTS
The r e s u l t s o f a l l f i e l d and labora tory evaluat ions are presented
i n t h i s sect ion.
f i r s t , fo l lowed by the p a r t i c u l a t e emission and opac i t y data f o r each source.
Pre l im inary measurements i nc lud ing t rave rse p o i n t desc r ip t i on are given i n
Appendix A and Appendix 6.
Gas composit ion r e s u l t s f o r each source are presented
The r e s u l t s have been ca l cu la ted on a CDC 3300 computer using stan-
dard Fo r t ran programs. EPA-published equat ions have been used as the bas i s
o f t h e c a l c u l a t i o n techniques i n these programs. I t should be noted i n i n -
t e r p r e t i n g these r e s u l t s t h a t t h e p a r t i c u l a t e emission ra tes have been ca lcu-
l a ted by both t h e "concentrat ion x f low" and the " r a t i o of areas" methods
and t h e average repor ted. The average i s t h e bes t est imate o f t he t r u e value,
s ince the b i a s in t roduced by an i s o k i n e t i c sampling i s approximately equal b u t
o f opposi te s i g n i n t h e two c a l c u l a t i o n techniques and thus cancels i n t h e
average.
6
I JOB: EXCO - NORTH THUNDERBIRD INTERPOLL REPORT NO. 9-658
3.1.2 TEST NO. 2 CRUSHER IlUMP POCKET DISCHARGE
RESULTS OF GAS ANALYSES -- METHO11 3 (PERCENT BY VOLUME)
DATE O F RUN
DRY BASIS (ORSAT)
CARBON DIOXIDE
OXYGEN
CARBON MONOXIDE
NITROGEN
WET BASIS (ORSAT)
CARBON DIOXIIlE
OXYGEN
CARBON MONOXIDE
NITROGEN
HOISTURE CONTENT
DRY MOLECULAR WEIGHT
WET MOLECULAR WEIGHT
SPECIFIC GRAVITY (RELATIVE TO AIR)
RUN 1
1 0 / 2 3 / 7 9
e 03
20.90
0
79 .07
e 03
20 t 6 3
0
78 05
1 .29
28 0 84
28.70
,9924
RUN 2
1 0 / 2 4 / 7 9
03
20 .90
0
7 9 07
03
20.68
0
7 8 + 22
1.07
28 .84
28.72
,9922
RUN 3 i i
10/24 /79
03
20.90
0
79 .07
03
20 68
0
7 8 22
1.07
28 e 84
28.72
4 9922
$X CONDENSED WATER VAPOR IN GAS STREAM; MOISTURE CONTENT CALCULATED FROM AVERAGE STACK GAS TEMPERATURE ASSUMING SATURATION,
i
9
L
,., i i
1NTEF;FOl.L REFORT NO, 9-658 -1 JOB: EXCO - NORTH THUNDERBIRD
i TEST NO. 1 COARSE CRUSHER DISCHARGE 3.1.1
RESULTS OF GAS ANALYSES -- METHOD 3 (FERCENT BY VOLUME)
DATE OF RUN
DRY BASIS (ORSAT)
CARBON DIOXIDE
OXYGEN
CARBON MONOXIDE
NITROGEN
WET BASIS (ORSAT)
CARBON D I O X I E I E
OXYGEN
CARBON noNoxIrtE
NITROGEN
DRY MOLECULAR WEIGHT
WET MOLECULAR WEIGHT
SPECIFIC GRAVITY (RELATIVE TO A I R )
RUN 1
1 0 / 2 3 / 7 9
03
20 .90
0
79 4 07
+ 03
20 62
0
78 .01
. 7 . 4 & t U-I
28 6 8 4
28 70
,9912
RUN 2 RUN 3
1 0 / 2 3 / 7 9 10 /23 /79
4 03
20 .90
0
79 .07
03
20.62
0
78 .01
28 84
28 e 70
,9912
+ 03
20 4 90
0
7 9 07
e 03
20 62
0
78 .01
28 84
28.70
,9912
** CONDENSED WATER VAPOR I N GAS STREAM) MOISTURE CONTENT CALCULATED FROM AVERAGE STACK GAS TEMPERATURE ASSUMING SATURATION.
3.2 Results of Particle Concentration Determination
I 1 1
JOB: EXCO - NORTH THUNDERRIRD INTERFOLL REPORT NO. 9-658
3 . 1 . 3 TEST NO. 3 NORTH LOADING TUNNEL
RESULTS OF GAS ANALYSES -- METHOD 3 (PERCENT BY VOLUME) RUN 1 RUN 2 RUN 3
DATE OF RUN 1 0 / 2 4 / 7 9 1 0 / 2 4 / 7 9 1 0 / 2 4 / 7 9
DRY BASIS (ORSAT)
CARBON DIOXIDE + 0 3 t 03 03
OXYGEN 20 + 90 20 t 90 20 90
CARBON MONOXIDE 0 0 0
NITROGEN 7 9 e 07 79 .07 79 07
WET BASIS (ORSAT)
CARBON DIOXIDE 03 0 3 03
OXYGEN 20.72 20 + 72 20 72
CARBON MONOXIDE 0 0 0
NITROGEN 78 37 78 .37 78.37
DRY MOLECULAR WEIGHT 28 * 84 28 84 28 .84
WET MOLECULAR WEIGHT 28.75 28 75 28 75
SPECIFIC GRAVITY (RELATIVE TO AIR) t 9929 ,9929 9929
** CONDENSED WATER VAPOR IN GAS STREAM; MOISTURE CONTENT CALCULATED FROM AVERAGE STACK GAS TEMPERATURE ASSUMING SATURATION,
i 10
JOB: EXCO - NORTH THUNDERBIRD INTERPOLL REPORT NO. 9-658
JEST NO* L CRUSHER DUMP POCKET DISCHARGE 11 3 .2 .2 1
I .. .- -
RESULTS OF PARTICLE CONCENTRATION DETERMINATION -- METHOD s(BE)
I I
I 1 I 1 1 I 1 I I I I I E
I I
RUN 1
DATE OF RUN 10/23/79
TIME RUN START/END(HRS) 1718/1835
PITOT TUBE COEFFICIENT
TOTAL MOISTURE IN GAS SAMPLE (GRAMS)
TOTAL PARTICULATE MATER- IAL COLLECTEDCGRAMS) *
VOLUME THROUGH GAS METER (CF AT METER COND.)
TOTAL SAMPLING TIME (MIN)
NOZZLE DIAMETER (IN)
AVERAGE STACK GAS TEMPERATURE DURING DETERMINATION (DEG-F)
VOLUMETRIC FLOW**
ACTUAL * . e * * * + . . (ACFPO DRY STANDARD 4 , . (DSCFII)
ISOKINETIC VARIATION ( X )
PARTICLE CONCENTRATION.
ACTUAL + + . e . + . + . (QR/ACF) DRY STANDARD (QR/DSCF)
PARTICLE MASS FLOW ( L W H R )
,844
13.0
,0158
46.28
72.0
.243
50
39818 38201
104.1
.0050 ; 0052
1 +73
RUN 2 RUN 3
10/24/79 10/24/79
955/1100 1230/1335
4 844 * 844
10.8
,0128
45 .75 '
72.0
243
45.
39585 38440
10.7
0237
45.58
72.0
243
45.
AUL. 39371 ?plLjsr 38232
103.8 103.5
,0041 0076 e 0 0 4 2 0078
1 .42 2.61
I DRY CATCH ONLY It CALCULATED ON THE BASIS OF VELOCITY PRESSURES MEASURED
DURINQ THIS PARTICULATE DETERHINATION.
13
~
JOB: EXCO - NORTH THUNDERBIRD
INTERPOLL REPORT NO. 9-658
3.2.3 TEST NO. 3 NORTH LOADING TUNNEL I I RESULTS OF PARTICLE CONCENTRATION DETERMINATION -- METHOD BE)
1 1 1 I 1 1 I I 1 1
DATE OF RUN
TIME RUN START/END(HRS)
P ITOT TUBE COEFFICIENT
TOTAL MOISTURE I N GAS SAMPLE (GRAMS)
TOTAL PARTICULATE MATER- IAL COLLECTED (GRAMS) *
VOLUME THROUGH GAS METER ( C F AT METER COND.)
TOTAL SAMPLING TIME ( M I N )
NOZZLE DIAMETER ( I N )
AVERAGE STACK GAS TEMPERATURE DURING DETERtiINATION (DEG-F)
VOLUMETRIC FLOW$*
ACTUAL + * * + . . + + a (ACFM) DRY STANDARD , , , (DSCFM)
ISOKINETIC VARIATION ( X )
PARTICLE CONCENTRATION
ACTUAL . + + + . . * + + (GR/ACF) DRY STANDARD (GR/DSCF)
PARTICLE MASS FLOW (LR/HR)
RUN 1 RUN 2 RUN 3
10/24/79 10/24/79 10/24/79
740/ 843 1110/1212 1618/1720
870
8.3
,0130
42 t 98
60.0
-184
40 *
38425 37809
100.9
004s 0046
1 *49
t 870
8 .4
,0114
43 30
60.0
184
4 0 e
-- --- JU.(JT
37822
102.0
0039 e 0040
1.30
870
8.3
,0122
43 44
60.0
,184
4 0
&Qb.
io0 4
0042 + 0043
1 e40
DRY CATCH ONLY 4% CALCULATED ON THE BASIS OF VELOCITY PRESSURES HEASURED
DURING T H I S PARTICULATE DETERHINATION*
1 4
i
1. ;
1 1 I I
I I I I I 1 . 1 1 I I I 1 I I I
3.3 Results o f Opacity Determinations
15
JOB: EXCO - NORTH THUNDERBIRD
INTERPOLL REPORT NO. 9-658
TEST NO. 1 SOURCE: COARSE CRUSHER DISCHARGE 3.3.1
RESULTS OF OPACITY OBSERVATIONS - EPA METHOD 9
PERCENT OPACITY _ _ _ _ ~
0 5 IO 15 20 25 30 35 40 45 50 55 m 65 70 15 80 85 90
95
I 00
OPTICAL DENSITY
0 .0223 .0458 .0706
.0969
.I249
.I549
.I871
.2219
.2596
.3010
.3468
.3979
.4559
.5229
.602 I
.6990
.e239 I .ooo I .30l
: OBSERVER: .:
RELATIVE FREQUENCY ( % I
100
0
0
0
0
0
0
0 0 0
0 0 0 0
0
0
0
0
0 0
0
TIME AVERAGE
'' CERT I F I CAT I ON DATE : 6-6-19
DATE OF OBSERVATION: 10-23-79
TIME OF OOSERVATION: 0815-0915
16 S - 0 0 8 3 RR
JOB: EXCO - NORTH THUNDERBIRD
INTERPOLL REPORT NO. 9458
TEST NO. 2 SOURCE: COARSE CRUSHER DUMP POCKET . ._ 3.3.2
RESULTS OF OPACITY OBSERVATIONS - EPA METHOD 9
PERCENT OPAC I T
0
5 I O
15 20 25 30 35 40 45 50
55 60 65 70 75 80 85 90
95
I O 0
I .ORSERVER: ..
OPTICAL DENSITY
0 .0223 .0458 .0706 .0969 .I249 . I549 .I871 .2219 .2596 .3010
.3468
.3979
.4559
.5229
.6021
.6990
.82 39 I .ooo I .30l
E. TROWBRtDGE "CERTIFICATION DATE: 6-6-79
DATE OF OBSERVATION: 10-24-79. TIME OF OBSERVATION: 1340-1440
17
RELAT I VE FREQUENCY ( 5 1
65 35 0
0 0
0 0
. o 0 0 0
- 0 ,.
TIME AVERAGE
S-0083RR . .
i 1 I
I I
1 I 1 1 I I 1 1 I 1 1 I 1 I
I I
JOB: EXCO - NORTH THUNDERBIRD
INTERWLL REPORT NO. 9-658 1
, I
3.3.3 TEST NO. 3 SOURCE: NORTH LOADING TUNNEL
RESULTS OF OPACITY OBSERVATIONS - EPA METHOD 9
'ERCENT OPAC I TY
0
5
I O
15
20
25
30
35
40
45
50 55
60
65
70
75
80
85
90
95
IO0
IPTICAL DENSITY
0
.0223
.0458
.0706
.0969
.I249
. I549
. I871
.2219
.2596
.3010
.3468
.3979
.4559
.5229
.602 I
.6WO
.82 39
I .ooo I .30l
. OBSERVER: E. TROWBRIM;€
' I CERT I F ICAT I ON DATE : 6-6-79
DATE OF OBSERVATION: 10-23-79
TIME OF OBSERVATION: 1510-1610
18
iELATlVE FREQUENCY ($)
100
0 0
0 0 0
0
0
0 0 0 0 0
0
0
0 0 0
0 0 0
TIME AVERAGE
S-0083RR