SOURCE TEST AT U.S. STEEL
CLAIRTON COKE OVENS

CLAIRTON, PENNSYLVANIA

by

M. W. HARTMAN

Contract No. 68-02-2812
Assignment No. 23

EPA Technical Manager: Gene Riley

Prepared for:

U. S. Environmental Protection Agency
Emission Standards and Engineering Division
Emission Measurements Branch
Research Triangle Park, NC 27711

TRW Environmental Engineering Division
3200 E. Chapel Hill Rd./Nelson Hwy.

P. 0. Box 1300D
Research Triangle Park, NC 27709


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GLOSSARY

BaP	- Benz-a-Pyrene

BSO	- Benzene Soluble Organ!cs

DSCM	- Dry Standard Cubic Meters

GC	- Gas Chromatograph

MeCl	- Methylene Chloride

MS	- Mass Spectrophometer

PAH	- Polynuclear Aromatic Hydrocarbons

POM	- Polycyclic Organic Matter

SASS	- Source Assessment Sampling System

SAMPLE LABELING GLOSSARY

CD - Module Condensate

CICD - Impinger Contents

CIMC - Methylene Chloride Impinger Rinse

MR - Module Rinse Methylene Chloride

NMC - MeCl Nozzle Rinse

NPR - Nozzle Probe/Filter Rinse

P - Combined Probe

PF - Filter

PIB - Probe/Impinger Benzene Rinse

PICD - Probe/Impinger Condensate

PR - Probe/Filter Rinse

V - Vent Rinse

VB - Benzene Vent Rinse

VMC - Vent Rinse Methylene Chloride

XR - XAD-2 Resin


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TABLE OF CONTENTS

PAGE

1.0	INTRODUCTION			1

2.0	SUMMARY 	 ..... 		2

3.0	DESCRIPTION OF RESULTS		 .	5

4.0	PROCESS DESCRIPTION ....... 		8

5.0	LOCATION OF SAMPLING POINTS ...... 		12

6.0	TEST PROCEDURES 				14

APPENDIX A:	COMPLETE RESULTS AND SAMPLE CALCULATIONS

APPENDIX B:	LABORATORY RESULTS

APPENDIX C:	FIELD DATA SHEET

APPENDIX D:	TEST LOG

APPENDIX E:	PROJECT PARTICIPANTS


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1.0 INTRODUCTION

During the week of July 30 through August 6, 1978, TRW Environ-
mental Engineering Division, under Contract No, 68-02-2812, with the
Environmental Protection Agency's Emission Measurement Branch, tested a
battery of coke ovens at U.S. Steel's Clairton, Pennsylvania plant. The
purpose of this sampling was two-fold; 1) to provide data associated
with emissions of polycyclic organic matter from topside leaks and 2) to
verify that a reduction in visible topside emissions would result in an
emissions reduction of polycyclic organic material.

Sampling was conducted in order to determine the emission rate
(mg/min) of pollutants from a simulated coke oven topside leak; two
different size leaks were tested. In addition, background ambient
samples were taken from battery topside. The leaks were simulated by
modifying an oven port lid to include a vent tube which utilized a ball
valve for controlling the leak rate. Samples were collected by placing
the nozzle of the sampling train probe directly above the vent tube.
Pollution emission rates were determined for Benzene Soluble Organics
(BSO), Polycyclic Organic Matter (POM), and Benz-a-Pyrene {BaP); determi-
nation of a Benzene emission rate was attempted but was not successful.

1


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2.0 SUMMARY

During the week of testing at the Clairton Coke Works, seven sam-
ples of BSO/POM were taken from the simulated oven leaks on Battery
Number 1. In addition, two ambient air samples were taken at the
battery topside to provide information on the background pollutant
level. During each run the simulated leak was adjusted to give either a
large leak (approximately a three to six-foot visible plume) or a small
leak (approximately a one-foot visible plume). Tests one through four
were taken during a large leak while tests five through seven were taken
during a small leak. Photographs of the sampling apparatus and the
simulated leaks were taken during the test program for EPA by U.S. Steel
personnel; these photographs are on file at the EPA. All sampling was
done on the number one coke oven battery at the Clairton Plant. In
order to minimize problems with taking the sampling equipment onto the
hot battery topside, the ovens closest to the pinion wall were selected
for testing. In all cases, the oven lid closest to the push side of the
battery was used. Sampling was begun between the first and second hours
after the oven was charged. The ambient samples were taken on battery
topside past the pinion wall (i.e., between oven A-l, and the end of the
battery); this position was approximately 40 feet from the simulated
leak. A more detailed discussion of the sampling locations is presented
in Section 5. A Summary of Results are shown in Table 2.1.

Separate sampling trains were used for the BSO and the POM/BaP
sampling. In order to obtain comparable BSO/POM data, a common nozzle
was used so that both trains could simultaneously sample the same leak
The sampling rates were adjusted so that approximately half of the leak
went to each train. Both trains were of a modified Source Assessment
Sampling System (SASS); SASS trains were used in order to obtain a high
sample rate.


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¥

1

2

3

4

5

6

7

5ft

58

7A

5A

SB

i

SUMMARY OF RESULTS

ISO

£





&

h"





in

te

M

5

a

us
h-

s

S

U!
_4

12:50

8/2

^ III

Larne

14:23

8/2

A I

Large

8:35

8/3

A V

Large

10:16

8/3

A VII

Large

12:53

8/4

A 11

Small

21:32

8/4

A I

Small

16:45

8/5

A I

Small

12:33

8/4

Ambient

None

21:12

8/4

Ambient

None

15:07

8/5

Ambient

None

24

6

15
8

16

15
15
56
55
70

784
1700
881S
1618
458
714
1312

9.3
9.0

283.33

587.93
202.25
28.63
47.60
87.47

0.084

l«r.fi4
0.118
1.069
0.148
0.672
0.730
0.604

9.988

0.128 6.709

30
9
15
10
15
15
15
55
55
69

2189

511

7.6

218,9

34.0

1,873
0.131
0.637
0.404
0.823
0.880
0.803
9.608

0.11 6.347

35.83 3.58

17.91 1.19

0.12 0.0017

Collected During Run 5
Collected During Run 6

Table 2.1. SUMMA.PY OF RESULTS


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POLTCYCLIC ORGANIC MATERIAL ANALYSES



BAP 4

BAP 7

BAP 7A

COMPOUND

MOLECULAR WT.

MASS (tug}

EMISSION
RATE (mg/min)

MASS (mg)

EMISSION
RATE (mg/min)

MASS (mg)

EMISSION
RATE (mg/mii)

NAPHTHALENE

128

320.2

32.0

138.8

9.2





DIPHENYL

154

13.6

1.4

3,1

0.2





DIMETHYLNAPHTHALENES

156

10.1

1.0

1.6

0.1





ACENAPHTHYLENE

152

128.8

12.3









DIBENZOFURAN

168

71.8

7.2









FlUORENE

166

81.0

8.1

15.4

1.0





DIMETHYLSI PHENYLS

182

18.3

1.8









DIBENZOTHIOPHENE

184

21.2

2.1

2.0

0.1





PHENANTHRENE

178

374.0

37.4

55.2

3.7

3.1

0.045

BENZO(h)QUINOLINE

179

4.4

0.4









CARBANZOLE

167

44.§

4.5









METHYLPHENANTHRENE

192

33.8

3.4

4.3

0.3





4H-CYCL0PENTA

(def) PHENANTHRENE

190

32.0

3.2









PHENYLNAPHTHALENE

204

9.2

0.9









PYRENE-

202

153.8

15,4

31.9

2.1

1.4

0.020

FLUORANTHENE

202

146.2

14.6

30.0

2.0

0.7

0.010

BENZO(a)FLUORENE

216

26.6

2.7

5.9

0.4





METHYLPYRENES

216

46.2

4.6

10.2

0.7





BENZO(ghi)FLUORANTHENE

226

9.8

1.0









CHRYSENE

228

8.5

0.8

65.9

4.4





BENZ0(3)ANTHRAcENE

228

150.0

15.0









TERPHENYL "

230

5.4

0.5









METHYLBENZOANTHRALENES

242

29.4

2.9

10.6

0.7





BENZOTHIOPHENE

240

18.7

1.9









BEN20PYRENES

242

296.1

29.6

135.7

9.0





BENZOPERYLENES

276

109.8

11.0





2.4

0.035

DI8ENZ0ANTHRACENE

278

24.7

2.5









TOTAL POM



2188.5

218.8

j 510.6

33.9

7.6

o. no

TABLE 2.2. POM ANALYSIS


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The BSO fraction was passed through a dry impinger into a filter at
125°F. The filter and first impinger contents were extracted with
benzene; the extract was dried and the BSO determined gravimetrically.
The filtered gas flow proceeded through three more impingers containing
water and finally through silica gel before being measured at the meter
box. The impingers were extracted with benzene which was dried and
weighed.

The POM/BaP fraction was collected on a filter at 125°F and a solid
adsorbent resin (XAD-2) which were both extracted with methylene chloride
(MeCl). The gas then passed through a series of impingers containing
water and silica gel before being measured on the gas meter. The re-
covered water was extracted with MeCl. POM analysis was conducted on a
Gas Chromatograph/Mass Spectrometer (GC/MS) - by TRW's West Coast Ana-
lytical Department. The BaP analysis was conducted at the EPA1s Research
Triangle Park location by thin layer chromatography/f 1 uorescence. Only
runs 4, 7 and 7A were analyzed for POM/BaP. For the remaining runs the
samples were extracted and the extract retained for possible future
analysis.

An integrated bag was taken after the filter from the BSO stream.
It was analyzed on-site for benzene with a gas chromatograph. The
benzene results are missing from this report since it was determined
that the high concentrations of the volatile organic matter present in
the sample made the determination of benzene impossible. The gas chro-
matography column utilized in the field on the integrated bag sample did
not perform an adequate separation of benzene from the interfering
compounds.

5


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3.0 DISCUSSION OF RESULTS

Upon arrival at the plant the van was set up next to the coke
ovens. Generators were rented in order to provide power for the SASS
trains. The vent pipe was placed on an oven lid. The orifice plate
(Section 6) in the vent pipe not only caused a flow restriction but also
provided a flat surface on which tar formed a viscous layer resulting in
complete plugging of the vent in a short period of time. The orifice
plate was removed and a larger steadier flow resulted. All tests were
conducted without an orifice plate. Prior to the first run a problem
was encountered with plugging of the leak vent which seemed to be caused
by particles of coal fines. A new vent was placed on the lid and the
first test conducted. Although the leak vent did not totally plug
during the test* the flow appeared to be somewhat restricted. The
determination was made that this problem of flow restriction due to coal
fines would occur only during the first hour of testing, therefore
subsequent tests were begun one hour after oven charging. The partial
plugging of the vent is reflected in the results. The first test was of
longer duration (24 minutes) and collected less mass than the subsequent
tests at the large leak rate. The first test was considered an experiment
and three more complete tests were conducted. During the sampling the
probe nozzle was placed one half inch above the vent outlet to permit
visual monitoring of the leak. The observation of the leak assured that
plugging of the vent did not occur during the tests runs.

SASS trains were used to collect the sample. The POM/BaP train and
the BSO train used a common nozzle which was placed above the
simulated leak. After a photograph of the leak was taken, the
test was initiated. The pumping rate was adjusted so that each train

6


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sampled an equal amount and the entire leak was captured. The tests
were of a short duration due to the plugging of the filters on each
train. The runs were discontinued when the filters were overloaded.
The flow rates were adjusted by timing the volume and observing the
meter orifice pressure differential. This was not an accurate process;
therefore, the volumes collected were not exactly equal. The valve that
adjusted the leak was a coarse ball valve which only permitted approx-
imately the desired leak rate. The variability in the leak rate accounted
for the different sampling times.

The filter was placed on the wrong side of the supporting screen
during run 3 in the BSO train. This accounts for the large sampling
volume and mass collected. The sample volumes of run 4 disagree by a
factor of four. No apparent reason is known for this other than they
were both low volumes and this type of variance in flow rate could
easily have resulted from the flow approximating method.

Methylene chloride was to have been used as an impinger solvent,
however, during the first attempted leak check it was found to be
freezing the impingers at the tips and causing plugging. Water was
substituted and used in all the tests.

The ambient trains were operated approximately 40 feet away from
the oven lids. The ambient test runs were started before the BSO/POM
tests and were stopped after the sampling. Duration and volume sampled
were greater than the lid leak tests in an attempt to produce a measureable
sample.

Immediately following each test the samples were recovered. The
recovered samples were transported to TRW's west coast facilities where
the splitting, combining, extraction and analysis took place. MeCl was
used to rinse the sampling equipment as well as for the extraction of
the POM train filter and Resin. The complete results of the GC/MS
analysis are contained in Appendix B. Only samples 4, 7 and 7A were
analyzed for POM/BaP. The sample splits of these samples were sent to
EPA at Research Triangle Park, North Carolina. Where thin layer chromato-
graphy /spectroscopy for Benz-a-Pyrene analysis were performed. These
results are 1isted in Appendix B. For all other runs the samples were
extracted and the extract retained for possible future analysis.

7


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During testing, an integrated bag was collected from the BSO train
after the filter. This bag was analyzed on site for benzene utilizing
an 0V-101 column on a dual flame ionization detector gas chromatograph.
The resulting chromatogram displayed numerous peaks in the retention
time frame of benzene. These peaks made it impossible to discern which
peak was benzene or if benzene was masked by the interfering peaks.

Although different column conditions were attempted, the high concentrations
of volatile organic matter present in the sample rendered separation
impossible. No benzene results are presented here.

Multiple extractions were performed on the BSO samples (filter) to
determine the efficiency of the first and subsequent extractions. The
average of the first extractions were 98.8% of the total with the remaining
1.2% present in the second extraction. No weight gains were recorded
for the third extraction. Complete results are listed in Appendix B.
Multiple extractions with Methylene chloride were conducted on filters
and resins for several POM samples in order to determine the efficiency
of extraction. The first extraction contained 99.9% of the measurable
POMs and the second extract the remaining 0.1%. The third extractions
were below detection limits. Furthermore, cyclohexane extractions were
conducted on several samples after the MeCl extraction to determine the
efficiency of the MeCl extraction. The BaP cyclohexane extractions were
below the detection limits.

8


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4.0 PROCESS DESCRIPTION

Battery 1 is one of three batteries (1, 2, 3) of a coke overi oper-
ating facility located at the Clairton works. Table 1 lists design
parameters of Battery 1.

During the testing, Battery 1 was operated in a normal manner. The
average gross coking time was 18 hours. Table 2 lists the production
rates for each day of testing. Table 3 lists coal analyses (conducted
by U.S. Steel) for each day of testing.

9


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TABLE 1

COKE OVEN BATTERY DESCRIPTION"

1

Type

Number of ovens

Date of initial operation

Date of last pad up rebuild

Approximate oven width (average)

Approximate oven height (floor to roof)

Approximate oven length (between doors)

Free space above coal

Calculated capacity (cubic foot coal)

Charging holes

Charging hole diameter

Number of collecting mains

Type of oven doors

Type of charging

Wilputte

64
1918
1955
18.5 inches
11 feet 10 inches
37 feet 4 inches
13 inches
626
4 per oven
18 inches
2

self-sealing

gravity feed stage charging

1Information from letter of September 6, 1974 from John G. Munson,
Assistant to Vice President of U.S. Steel, to Reid Iversen, EPA.

10


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TABLE 2
PRODUCT INFORMATION

l

Date	Ovens Charged Per Da.y	Gross Coking Time (hrs)

8/1/78

81

19.0

8/2/78

83

18.5

8/3/78

73

21.0

8/4/78

83

18.5

8/5/78

82

18.7





19.1

i

Information from letter of September 18, 1978 from R.J. Weiskircher
of U.S. Steel to C.E. Riley, U.S. EPA.

11


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TABLE 3: COAL ANALYSIS1

Screen Size

%H„0

%Sulphur

%Ash

CTolatiles

+.500

+.250

+ .125

-.125



C





inch

inch

inch

inch

8/1/78

6.5

1.15

7.45

28.80

4.6

14.8

17.1

63.5

8/2

6.3

1.21

7.75

28.75

3.0

14.9

16.3

65.8

8/3

6.2

1.14

7.65

29.60

4.3

13.6

16.7

65.4

8/4

5.9

1.15

7.80

29.40

5.7

14.2

15.4

64.7

8/5

6.8

1.16

8.25

29.15

4.7

15.0

15.3

65.0

information from letter of September 18, 1978 from R.J. Weiskircher of U.S. Steel to C.E. Riley,
U.S. EPA.


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5.0 LOCATION OF SAMPLING POINTS

All sampling points were located on the topside of the number one
coke oven battery at the Clairton Works. The oven charging port closest
to the push side was chosen for sampling. One end of the oven battery
was chosen because it would least disturb the normal operation of the
charging trolley. All samples were taken from ovens Aj through A^,
depending upon the daily charging sequence. The ambient samples were
taken from topside at a location past the pinion wall. Figure 5.1 is a
schematic of the battery topside indicating the sampling locations.

13


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•SAMPLE POINT

O

o

o
o

PUSHING
SIDE

O

o
o

EXHAUST FUME
COLLECTOR



AfiO

«4 0

A3 (ft

A2(£

A,®

1

OVERHEAD TROLLEY

O

o
o

o

G
O

o

o

o
o

G
O
G
G

3

ROOF HEIGHT-30' ABOVE GROUND LEVEL

PINION WALL

AMBIENT SAMPLE •

SAMPLE TRAIN
PREPARATION AREA

G

O
O

G

("")

V_-r'

G

o

4

C2qG

o

o

o

COKING SIDE

40'

FIGURE 5.1 : BATTERY 1 (TOPSIDE VIEW)

1A


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6.0 TEST PROCEDURES

During the testing, the oven was charged with the overhead trolley
and the lids replaced and sealed by U.S. Steel personnel; a special lid
modified with a valve and vent pipe was replaced on one of the oven
ports (see Figure 6.1). After the lids had been sealed, a simulated
leak was attempted at the desired plume length. Condensation occurred
in the vent forming a viscous substance; consequently, the plume was
monitored continuously to assure clogging of the vent did not occur.

Once the plume was determined to be the correct size, the nozzle was
placed over the vent and the sampling trains were started. During
sampling, the vent was visually monitored continuously to assure that
the sampling rate was sufficient to assure total capture of the leak.
Sampling was continued until plugging in the vent occurred or until the
loading on the sample train filter caused an excessive decrease in the
sampling rate. The sampling rates of the BSO and POM sampling systems
were evenly maintained in order to evenly split the sample between the
two trains.

The sampling was conducted in accordance with the draft methods--
Determination of Benz-a-Pyrene Emissions from Stationary Sources and
Determination of Benzene Soluble Organics. Both of these methods were
supplied by EPA and both are draft procedures. Several exceptions to
the procedures of these Methods were made. SASS sampling trains were
substituted for the regular Method 5 trains and the two sampling trains
shared a common nozzle (see Figure 6.2). The ambient air sampling
system was a Method 5 train modified to accept the XAD-2 adsorbing
module; no nozzle was used for this train. Methylene chloride was not
used in the impingers because of a problem in freezing due to the heat
loss inherent in volatile organic compounds. This was determined during
the first run. Subsequent impinger fractions used water as a collection

15


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medium. Methylene chloride was used for cleanup and extraction of the
POM train in lieu of cyclohexane.

The basic sample train components are diagrammed in Figure 6.3.
All the components used were standard source assessment sampling system
(SASS) parts. A simulated leak was created by the pressure in the oven
flowing through the valve to the atmosphere. After visually measuring
the leak a nozzle common to both trains was positioned over the leak.
The nozzle was not connected but just positioned over the leak. The
train's pumps were adjusted to provide approximately half the leak to
each sample train. Some excess air was also sampled to insure all of
the vent gases were captured. The probe and heated oven were maintained
at 125°F for the BaP/POM train while only the probe was heated to 100°F
for the BSO train. The BaP/POM train filtered the sample to remove the
particulate matter. The non-particulate gases were then collected by
passing the gas sample through an XAD-2 absorbent resin maintained at
70-90°F. Cooled impingers and silica gel were used to collect the
remaining moisture prior to the pumps and the gas flow meters. The
BSO train collected the particulate in the first impinger and on the
filter. A dry impinger was placed prior to the filter in order to
minimize plugging. During the sampling, an integrated Tedlar bag was
taken after the impingers but before the silica gel on the BaP/POM
train. A sample identification log is contained in Appendix C. This
log lists each sample fraction and the solvent used in clean up and
recovery. They are generally shown in the following table. The GC/MS
analysis was performed according to the procedures outlined in Analysis
of Polynuclear Aromatic Hydrocarbons from Coke Oven Effluents by R. E.
Beimar, September, 1978 (EPA report 78-CK0-12). The Column utilized was
a Dexel 300 packed column for the separation of POMS!

16


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j ! S i \

common nozzle

l/2"Stain1ess Steel Tube
(Insulated)

1" Nipple Threaded
Into Oven Port

A

1" Stainless Steel Ball Valve

Figure 6.1 Sampling Vent/Probe Configuration


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Probe

Filter

Modified
Batelle Trap

Adsorbent

Sampler

XAD-2

lingers

¦N i



Pump Thermostated
1WF"

(HoO)

Inclined Manometer

laQ

Pump

Iry Gas Meter

FIGURE 6.2 AMBIENT TRAIN


-------
BSO TRAIN

To

Common Probe
Nozzle ^ 	

(Knock Out
Impinger

^>To Integrated Sampling Bag

Blank silip.

Inningers

Pumps
and

Control
Module

U3

To
Common
Nozzle



Probe

T

U

: Filter

XAD-2
Adsorbent
Module

POM/BaP Train

Inpi oners

Figure 6-3. SASS SAMPLING TRAINS


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Field Recovery of BSO Train

Component

Probe, Knock-out Impinger, Filter Housing
Filter

X

Impingers

Recovery Steps

Condensate collected
Acetone Rinse
Benzene Rinse

Collected

Condensate collected
Acetone Rinse
Benzene Rinse

Component
Vent Pipe

Common Nozzle

Field Recovery of BSQ/BaP Trains
(Common Components)

Recovery Steps

Methylene Chloride Rinse
Benzene Rinse

Methylene Chloride Rinse
Benzene Rinse

Field Recovery of BaP Train

Component

Probe, Front of Filter Holder

Filter

XAD-2 Resin

Back of Filter Holder and Module
1

Impingers

Recovery Steps
Methylene Chloride Rinse
Collected
Collected

Condensate Collected
Methylene Chloride Rinse

Condensate Collected
Acetone Rinse
Methylene Chloride Rinse

1

Some Impingers contained activated charcoal which was not recovered
after each test. The same is true of the silica gel.

20


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Laboratory Sample Preparation
(BaP/BSO Common Fractions)

1.	Nozzle - Methylene Chloride Rinse - Split1

Benzene Rinse	- Split1

2.	Vent - Methylene Chloride Rinse split (A B C)

Benzene Rinse

Laboratory Sample Preparation
(BSO Fractions)	~

3

1.	Nozzle Benzene Rinse , Probe, and

Knock-out Impinger Benzene Rinse	Combine(j and Spm4 (D>E)

and Nozzle Methylene Chrloride Fraction

2.	Probe Knock-out Impinger Acetone Rinse - Split (D,E)

3.	Filter Benzene Extraction and Split (D,E)

4.	Impinger Liquid - Split (D,E)

5.	Impinger Acetone Rinse - Split (D,E)

6.	Impinger Benzene Rinse - Split (D,E)

7.	Knock-out Impinger Condensate - None in most cases

*The rinses split in a ratio to correspond to the sampled gas volumes of
the BaP/BSO trains for each test.

2

Nozzle fraction (Methylene Chloride) after being brought to dryness
and re-extracted with Benzene.

3Nozz1e fraction derived from the BaP/BSO common fractions.

4The samples were split in half. The "D" fractions were dried and
weighted gravimetrically by TRW. The "E" fractions were sent to EPA
and from EPA to U. S. Steel.

21


-------
laboratory Sample Preparation (continued)

(BaP/POM Sample Fractions)

5

*1. Nozzle - Methylene Chloride Rinse	g

Combined and Split (A,B,C)

Probe Front of Filter Holder Methylene Chloride Rinse

*2. Filter - First Methylene Chloride Extraction and Split (A,B,C)

-	Second Methylene Chloride Extraction and Split (A,B,C)

-	Third Cyclohexane Extraction and Split (A,B,C)

*3. XAD-2 Resin - First Methylene Chloride Extraction and Split (A,B,C)

-	Second Methylene Chloride Extraction and Split (A,B,C)

-	Third Cyclohexane Chloride Extraction and Split
' (A.BjC)

*4. Module Condensate - Cyclohexane Extraction and Split (A,B,C)

*5. Module Back of Filter Holder - Methylene Chloride Rinse and Split
(A,B,C)

6.	Impinger Liquid Cyclohexane Extraction and Split (A,B,C)

7.	Impinger Rinse Acetone Rinse	Combined and Split (A,B,C)

Methylene Chloride Rinse

5

From BaP/BSO common fractions.

£?

"A" which was half of the volume was aliquoted and GC/MS'd by TRW
(see note *.)

"B" which was a quarter of the volume was sent to EPA.

"C" which was a quarter of the volume was retained.

~Equal aliquots from the "A" fractions of the split for each section of
the sampling train were combined, except the samples derived from the
impingers, to provide a solution for GC/MS analysis. GC/MS was used
for runs BaP4, BaP7, and BaP 7A, the results are reported. Samples
from the other runs were kept but not analyzed.

22


-------
APPENDIX A
COMPLETE RESULTS AND SAMPLE CALCULATIONS


-------
1. (ex.)

Where: 45.4 »g
ml

Sample Calculations
Polyclclic Organic Material (Table 2,2)

Total Weight (mg of Dibenzofuran, Run 4

=71.8 mg

45.4 uQ X 1582 ml X 	

ml	1000 yg

m.

1582 ml

2.	(ex.)

Where: 71.8 mg
10 min,

3.	(ex.)

Where: 1383.4uq
ml

1582 ml

10 miri.

4. (ex.)

Where 35.83 mg

10 min
5. (ex.)

Where: 1.618 g

= GC/MS Analysis of Composite Sample Fraction of
BAP-4 from Smith Report

= Total Sample Volume of BAP-4

Emission Rate (mg/min.) of Dibenzofuran, Run 4

71.8 mg = 7.18 mg/min.

10 min,

= Total Weight of Dibenzofuran

= Total Run Time

Summary of Results (Table 2.1)

POM Emission Rate (mg/min), Run 4

¦ 1383.4 uq X 1582 ml = 218.85 mg/min
ml	10 min.

= Total weight of constituents in BAP-4 Run (see
Table 4.1: GC/MS Analysis - Smith Report)

= Total Sample Volume of BAP-4 Run

= Total Run Time of BAP-4

BAP Emission Rate (mg/min.), Run 4

= 35.83 mg = 3.58 mg/min.

10 min.

= Total mass of fractions from BAP-4 Run (see Clairton
Coke Oven Samples Benz-a-Pyrene Analysis - Rogers
Report)

= Total Run Time of BAP-4

BS0 Emission Rate (mg/min.) of Run 4

= 1*618 g X 1000 mg = 202.25 mg/min.
8 min.	g

= Total Mass of BS0-4 fractions from Gravimetric
Analysis in Smith's Report:


-------
i	I	K.

Sample Calculation (continued)

Fraction	Mass (Grams)

BS0-4-PF (First Filter Extraction)	0.8687

BS0-4-PF (Second Filter Extraction)	0.0108

BS0-4-CICD Impinger Condensate	0.0117

BS0-4-CIA Impinger Acetone Rinse	0.0059

BS0-4-PIA Probe Acetone Rinse	0.7151

BS0-4-CIB Impinger Benzene Rinse	0.0011

BS0-4-PIB Probe Benzene Rinse 		0.0047

Total BS0-4 Mass
8 min. = Total run time of BSO-4

1.618 Grams


-------
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-------
TECHNICAL DIRECTIVE

PREPARATION OF BAP/POM AND BSO SAMPLES
CLAIRTON COKE WORKS

The attached schedule outlines the specific details of how each
sample collected at the Clairton Coke Works is to be prepared and split
for analysis. The schedule is detailed as follows:

I.	Splitting nozzle/vent samples.

II.	Combining nozzle/probe rinse samples for BAP.

III.	BAP sample preparation and splitting.

IV.	Combining BAP sample fractions.

V.	Re-extraction of filter and resin with cyclohexane.

VI.	Combining BSO probe/nozzle samples.

VII.	Splitting BSO sample fractions.

VIII.	List of samples to be sent to EPA for TLC analysis.

IX.	List of samples to be sent to EPA for transmittal to U.S. Steel
Corp.

X.	List of samples for GC/MS analysis.

XI.	List of samples for BSO analysis.

XII.	List of samples to be retained for possible analysis at a future
date.

NOTES:

Prior to conducting this work, blank run analysis were conducted on MeCL,
cyclohexane and benzene to assure contamination was not present.

1.	Assure that splitting of the samples is done accurately to the
indicated fractions since split samples will be recombined before analysis
is conducted.

2.	Assure that samples are homogeneous prior to splitting. Use
ultrasonic agitation if necessary.


-------
3.	Prepare POM/BAP samples according to procedures outlined in
the draft test method for BAP except that methylene chloride shall be
used instead of cyclohexane (filter and solid resin extraction).

4.	Prepare and analyze BSO samples according to procedures
outlined in the draft test method for benzene soluble organics.

5.	Extract filter and resin according to procedures established
in the BAP method, paragraph 4.3, except that methylene chloride, in
lieu of cyclohexane, is to be used. Split the methylene chloride
extract; retain the filter and solid resin for re-extraction with
cyclohexane according to the procedures of paragraph 4.3 of the BAP
method.

6.	Extract the condensate according to the extraction procedures
of paragraph 4.3.3. of the BSO test method substituting cyclohexane
for benzene. (Do not filter or bring to dryness).

7.	Evaporate the sample to dryness and then redissolve the sample
residue^enzene. Combine this benzene solution as indicated.


-------
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-------
APPENDIX B
LABORATORY RESULTS


-------
ISO RESULTS

Run Number

~Total Mass (GR.)

Meter Volume (DSCF)

BSO-1

0.7843

58.74

BSO-2

1.6997

4.17

BSO-3

8.8190

37.75

BSO-4

1.6180

5.24

BSO-5

0.4578

23.73

BSO-SAB

0.0093

352.58

BSO-6

0.7143

25.77

BSO-7

1.3123

236.84

BS0-7A

0.0090

21.34

*The BSO Grams Total Mass is the sum of the partial
masses for the separate runs as presented in Table 2-1
Gravimetric Analysis of the Smith Report.


-------
UNITED STATES ENVIRONMENTAL PROTECTION AGENCY
RESEARCH TRIANGLE PARK, NORTH CAROLINA 27711

DATE: July 25, 1979
subject: Clairton Coke Oven Samples

TO Roy Neulicht

OAQPS, ESED (MD-19)

Attached is the information you requested. If I can be of further
assistance, please call.

Attachment

FROM: Crystal Rogers, Physical Scientist
SFMCS, PAB, EMD, EMSL/RTP (MD-78)

I PA Form 1320-4 (Rev. 3-76)


-------
CLAIRTON COKE OVEN SAMPLES

BENZ-a-PYRENE ANALYSIS

Sample Identification

SflMlPJ.'C. J V

H\f\ Ss C

BaP ng/ml

4-MPR-B

ZiZ



10,520

- 4-PF -B

Ito

]

37,600

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236.

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225*

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) (f U

\.t\l

10,920

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) V, w

O-O^lh

10

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1 1m



.— BMD**

4-MR -B

}°l In

pTs j

124,240



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7-NPR-B "

~t U> 1

7,777

10,640

7-PF -B

7 \0

|£.£>36

71,600

7-PF2-B

1(72

iJ1. OH

240

7-XR1-B

nt?



Received Empty

J-XR2-3 -

m



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}%



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• 7-MR -B

C Lj t\

.*"S

87

Mass Kn/sJ ^

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-

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o. i loi-

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T^u £A P- 7A RarJ

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BSO/BaP MCB-B





BMD

BSO/BaP XRB1-B





BMD

BSO/BaP XRB2-B





BMD

BSO/BaP XRB3-B





BMD

*4-PF2-B was run twice. A 1:1 dilution yielded a result of 225 ng/rnl
while a 1:200 dilution gave a result of 240 ng BaP/ml»

**BMD = Below Minimum Detection. For this case, less than TO ng BaP/ml.
Si	~ Sa^)c Vo'-rri ^ (L^ f" , ' ^ \ ^ ^^

d	W


-------
Analysis of U.S. Steel,
Clalrton Works Samples

Aug. 2, 1979
by

T. R. Smith

f rxww

atttHSt Am SMcr systems gmx*


-------
TABLE OF CONTENTS

Page

1.0 INTRODUCTION					 1

2.0 GRAVIMETRIC ANALYSIS			 2

3.0 SAMPLE SPLITTING AND COMBINATION ... 	 5

4.0 POLYNUCLEAR AROMATIC HYDROCARBONS .... 	 8

11


-------
List of Tables

Number	Page

2-1	Gravimetric Analysis ..... 	 .........	2

3-1	Sample Volumes ................. 		5

4-1	GC/MS Analysis 					8

%

111


-------
1.0 INTRODUCTION

This report represents the analysis performed on the samples originating
from the U.S. Steel, Clalrton Works.

Included are the gravimetric analysis results of the benzene soluble
organtcs tests. The volumes of the samples which were split and combined
are also presented. GC/MS analysis of several combined samples was also
performed and 1s presented In this report.

1


-------
2.0 GRAVIMETRIC ANALYSIS

The results of these analyses are compiled in Table 2-1
were handled in the following manner.

The samples

Sample Fraction
Filter

Sample Designations BSO Test Method Paragraph
BSO-X-PF*

1st Impinger (Acetone)
Probe (Acetone)
1st Impinger (Benzene)
Probe (Benzene)

BSO-X-CICD
BSO-X-PICD

BSO-X-CIA
BSO-X-PIA
BSO-X-CIB
BSO-X-PIB

4.3.2. (two six hour extractions
were performed)

4.3.3

(cyclohexane was substituted
for benzene)

4.3.4

4.3.5

Filter Paper

BS0-1-PF

BS0-2-PF

BS0-3-PF

BS0-4-PF

BS0-5-PF

BS0-5AB-PF

BS0-6-PF

BS0-7-PF

BS0-7A-PF

Table 2-1 GRAVIMETRIC ANALYSIS

First Extract
(grams)

0.4105
1.1766
0.4045
0.8687
0.2209
0.0005
0.2505
0.8682
0.0004

Second Extract
(grams)

0.0085
0.0156
0.0014
0.0108
0.0050
0.0004
0.0041
0.0029
0.0004

Combined Impinger Condensate (1st Impinger Only)



(grams)

BS0-2-CICD

0.0106

BS0-3-CICD

0.0528

BS0-4-CICD

0.0117

BS0-5-CICD

0.0013

BS0-5-CICD2

0.0001

BS0-5AB-CICD

0.0001

BS0-6-CICD

0.0054

* (-X-) Designates sample run number.

2


-------
Combined Implnger Condensate (continued)

(grams)

8SO- 7-CICD	0.0029

BS0-7A-CICD	0.0019

BS0-37-CICD	0.0812

BS0-37A-CICD	0.0142

BS0-1-PICD	0.0019 - Probe/Implnger Condensate

BS0-6-H20	0.0001

Combined Implnger Rinse/Acetone

{grams}

BS0-2-CIA	0.1277

BS0-3-CIA	3.4809

BS0-4-CIA	0.0059

BS0-5-CIA	0.0019

BS0-5AB-CIA	0.0013

BS0-6-CIA	0.0015

BS0-7-CIA	0.0090

BS0-7A-CIA	0.0022

*

Probe/Implnger Rinse/Acetone

(grams)

BS0-1-PIA	0.3390

BS0-2-PIA	0.3213

BS0-3-PIA	3.2108

BS0-4-PIA	0.7151

BS0-5-PIA	0.0042

BS0-5AB-PIA	0.0032

BS0-6-PIA	0.4326

BS0-7-PIA	0.4125

BS0-7A-PIA _	0.0013

„ ^SO-O-PIAB-l	0.0026

"* JiSO-O-PIAB-2	0.0013

3

Implnger = Greenburg/Smith Implnger


-------
Combined Implnger Rinse/Benzene



(grams)

BS0-1-CIB

0.0002

BS0-2-CIB

0.0017

BS0-3-CIB

1 .4625

BS0-4-CIB

0.0011

BSO-S-CIB

0.0031

BS0-5AB-CIB

0.0023

BS0-6-CIB

0.0007

BS0-7-CIB

0.0014

BS0-7A-CIB

0.0017

Probe Implnger Rinse/Benzene

(grams)

BS0-1-PIB	0.0242

BS0-2-PIB	0.0462

BS0-3-PIB	0.2052

BS0-4-PIB	0.0047

BS0-5-PIB	0.2213

BS0-5AB-PIB	0.0015

BS0-6-PIB	0.0194

BS0-7-PIB	0.0154

BS0-7A-PIB	0.0011

4


-------
3.0 SAMPLE SPLITTING AND COMBINATION

The samples were split and combined according to technical directive
Number 2. A listing of the sample designation and volume is included
as Table 3-1.

Table 3-1 Sample Volumes

e Designation

Volume

(ml)

BAP-1-NMC (MeCl Nozzle Rinse)

85



BS0-1-NMC

75



BAP-2-NMC

58



BS0-2-NMC

52



BAP-3-NMC

46



BS0-3-NMC

78



BAP-4-NMC

114



BS0-4-NMC

42



BAP-5-NMC

18



BAP-5-NMC

15



BAP-6-NMC

48



BS0-6-NMC

39



BAP-7-NMC

29



BS0-7-NMC

21



BA0-1-PR (Probe Rinse)

660



BAP-2-PR

124



BAP-3-PR

104



BAP-4-PR

128



BAP-5-PR

125



BAP-6-PR

138



BAP-7-PR

232



BAP-SAB-PR

52



BAP-7A-PR

72



BAP-l-CD (Module Condensate)

150



BAP-1-PF1 (Filter)

202

1st

BAP-1-PF2

250

2nd

BAP-1-PF3

138

3rd

BAP-2-PF1

228



5


-------
! 1	I

Table	3-1 continued

Sample Designation	Volume (ml)

BAP-5-XR2 (XAD-2 Resin)	196

BAP-S-XR3	190

BAP-5AB-XR1	136

BAP-5AB-XR2	200

BAP-5AB-XR3	184

BAP-6-XR1	120

BAP-6-XR2	188

BAP-6-XR3	200

BAP-7-XR1	176

BAP-7-XR2	194

BAP-7-XR3	196

BAP-7A-XR1	160

BAP-7A-XR2	184

BAP-7A-XR3	190
BAP-l-MR (MeCI Module Rinse) 230

BAP-2-MR	64

BAP-3-MR	328

BAP-4-MR	196

BAP-5-MR	484

BAP-5AB-MR	664

BAP-6-MR	912

BAP-7-HR	548

BAP-7A-MR	484
BAP/BS0-3-VMC (MeCI Vent Rinse) 260

BAP/BS0-7-VHC	136

BAP/BS0-3-VB (Benzene Vent	Rinse)112

BAP/BS0-7-VB	90

BAP-37-CIMC (MeCI Impinger	Rinse) 270

x

6


-------
Table 3-1 continued
Sample Designation	Volume (ml)

IAP-2-PF2 (Probe Filter)

244

BAP-2-PF3

130

BAP-3-PF1

184

BAP-3-PF2

242

BAP-3-PF3

116

BAP-4-PF1

188

BAP-4-PF2

236

BAP-4-PF3

184

BAP-5-PF1

204

BAP-5-PF2

204

BAP-5-PF3

132

BAP-6-PF1

214

BAP-6-PF2

198

BAP-6-PF3

236

BAP-7-PF1

210

BAP-7-PF2

202

BAP-7-PF3

214

BAP-7A-PF1

190

BAP-7A-PF2

234

BAP-7A-PF3

226

BAP-1-XR1 (XAD-2 Resin)

160 1st extraction

BAP-1-XR2

180 2nd extraction

BAP-1-XR3

180 3rd extraction

BAP-2-XR1

130

BAP-2-XR2

194

BAP-2-XR3

200

BAP-3-XR1

140

BAP-3-XR2

174 -

BAP-3-XR3

186

BAP-4-XR1

166

BAP-4-XR2

180

BAP-4-XR3

190

BAP-5-XR1

128

7


-------
4.0 POLYNUCLEAR AROMATIC HYDROCARBONS

The GC/MS analysis was performed according to the procedures used
in "Analysis of Polynuclear Aromatic Hydrocarbons from Coke Oven Effluents"
by R. G. Beimer, September, 1978 (EPA Report 78-CK0-12). The results
are listed in Table 4-1.

Table

4-1

GC/MS Analysis





M.W.

BAP 4

BAP 7





yg/mi

yg/ml

Naphthalene

128

202.4

70.4

Biphenyl

154

8.6

1.6

Dimethyl naphthalenes

156

6.4

0.8

Acenaphthylene

152

81.4



Dibenzofuran

168

45.4



Fluorene

166

51.2



Dimethylbiphenyls

182

11.6



Dibenzothiophene

184

13.4

1.0

Phenanthrene

178

236.4

28.0

Benzo(h)quinoline

179

2.8



Carbanzole

167

28.4



Methylphenanthrene

192

21.4

2.2

4H-Cyclopenta







(def)phenanthrene

190

20.2



Phenyl naphthalene

204

5.8



Pyrene

202

97.2

16.2

Fluoranthene

202

92.4

15.2

Benzo{a)fluorene

216

16.8

3.0

Methylpyrenes

216

29.2

5.2

Benzo(ghi)fluoranthene

226

6.2



Chrysene

228

5.4

33.4

Benzo(a)anthracene

228

94.8



Terphenyl

230

3.4



Methylbenzoanthracenes

242

18.6

5.4

Benzothiophene

240

11.8



Benzopyrenes

242

18.72

68.8

Benzoperylenes

276

69.4



Di benzoanthracene

278

15.6



TOTAL



1383.4

8

259.0

BAP7A
yg/ml

1.8

0.8
0.4

1.4

4.4


-------

-------
I


-------
APPENDIX C
FIELD DATA SHEETS


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-------
APPENDIX D
TEST LOG


-------
VIII FIELD TEST SCHEDULE
SATURDAY 7/29

SUNDAY 7/30

MONDAY 7/31
TUESDAY 8/1
WEDNESDAY 8/2
THURSDAY 8/3
FRIDAY 8/4

Personnel

Hartman
Moore
McReynolds
Henry
Carpenter
Wagoner

Hartman, McReynolds fly to Pittsburg. Henry and Carpenter
drive to Pittsburg. Arrive on site approximately 2:00PM
and begin set up of equipment.

Set up continues, blank clean up on trains and prep for
actual testing. Sunday evening Moore and Wagoner arrive
from West Coast.

A. M. Safety meeting, P. M. testing preparation

Test A. M. clean up, test P. M. clean up (pre-test runs)

Test A. M. clean up, test P. M. clean up

Test A. M. clean up, test P. M. clean up

Insure all samples are taken and catalogued, pack up and

go home.

Team Leader, supervisor, trouble shooter
Clean up manager, sample accountability, GC's

Team members-testing, clean up, sample recovery, etc.


-------
APPENDIX E
PROJECT PARTICIPANTS


-------
PROJECT PARTICIPANTS

Names

Company

Purpose

Gene Riley

EPA, Durham

Project Coordinator

Roy Neulight

EPA, Durham

Observe Test

Mike Hartman

TRW

Testing Team Leader

Dave Moor

TRW

Testing

Jim McReynolds

TRW

Testing

Gary Henry

TRW

Testing

Clay Carpenter

TRW

Testing

Dan Wagoner

TRW

Testing

Tyronne Smith

TRW

Testing


-------


(



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-------
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-------
ANALYSIS OF POLYNUCLEAR AROMATIC HYDROCARBONS FROM COKE OVER EFFLUENTS

This paper is a report on the Analysis of Polynuclear Aromatic
Hydrocarbons From Coke Oven Effluents. The program was conducted by TRW
for the Environmental Protection Agency, Emission Measurement Branch,

Research Triangle Park, North Carolina under Contract Number EPA
68-02-2812. Four samples taken from a coke oven at Republic Steel Cor-
poration in Gadsden, Alabama were used for methods development in poly-
nuclear aromatic hydrocarbon determination,

Polynuclear aromatic hydrocarbons (PAH), also referred to as
polycyclic organic matter (POM), are suspected of being serious health
hazards since some of the individual compounds are known carcinogens.

This class of compounds condense on particulate matter and can be inhaled
into the lungs or contacted with the skin. When coal is pyrolyzed by a
burning or coking process, significant amounts of PAHs are produced. In
the burning process most of the organic material is destroyed through
oxidation, producting water and carbon dioxide. In the coking process
however, significant amounts of organics are evolved and emitted to the
atmosphere. Many techniques exist for the determination of polynuclear
aromatic hydrocarbons. Specific compound analysis for PAHs of particular
interest or potency have been developed and are generally better than survey
analysis techniques. As an example, the determination of benzo(a)pyrene
can be accomplished quickly and accurately by thin layer chromatography
(TLC) with quantitation using variable wavelength fluorescence, a method

1

developed by the EPA . Other specific PAHs have been determined by liquid
chromatography using UV and/or fluroescence detection.

For general purpose determination of PAHs in complex mixtures the
use of gas chromatography-mass spectrometry is unexcelled. The gas chromato-
graph Is used to separate the complex mixture into individual component
peaks and the mass spectrometer is used as a detector for both qualitative
Identification of the PAH and for quantitative determination. In simple
cases where only a few PAHs are present, the use of packed gas chromatographic

""New Benzo(a)pyrene Analytical Method; EPA EMSL ACB SFMCS RTP N.C.:

Don Swanson et.al. (no date).

-1-


-------
columns are recommended. Packed columns are generally easier to use, re-
quire a shorter time for analysis, and are cheaper. When highly complex
mixtures of PAHs are present or significant interferences occur, the use
of capillary columns becomes necessary. Capillary column selection is
usually dependent on the volatility and polarity of the PAHs to be deter-
mi ned.

PAHs typically show very strong molecular ions (the mass representa-
tive of molecular weight) in their mass spectra because of the stability of
the aromatic system. The strong molecular ion allows for a very simple
identification of molecular weight even in complex mixtures. PAHs produce
very sensitive spectra when ionized in a mass spectrometer and can be
identified in a complex mixture quite easily. The disadvantage of this
strong molecular ion production is that isomeric PAHs produce spectra which
are virtually identical. The mass spectrometer is a rather poor device for
distinguishing isomers since once ionized the compound will seek its most
thermodynamically stable form. Since isomeric PAHs produce similar or
identical mass spectra the determination of structure is accomplished by
comparison of GC retention time using standards.

The major limitation of the gas chromatograph is the volatility of
compounds to be analyzed. In order to be determined, PAHs must produce
good chromatographic peaks at temperatures below 300°C. Above 300°C even
the most stable GC column liquid phases produce high background in the
mass spectrometer. This GC temperature limitation means that high molecular
weight PAHs (above MW=300) cannot be reliably determined by this technique.

A limited amount of work has been done in the determination of high
molecular weight PAHs using 1iquid chromatography. With a 1iquid chromato-
graph, the need for volatility does not exist and materials of virtually
any molecular weight can be determined. With the proper selection of
columns and the incorporation of a variable wavelength excitation and
detection fluorometer, PAHs can be determined with accuracy. Chromatographic
separation is not always required provided the excitation and detection wave-
length can be selected specifically for PAHs of interest. An example of a
liquid chromatographic determination of polynuclear aromatic hydrocarbons
will be presented.

-2-


-------
GC/MS RESULTS FROM COKE OVEN SAMPLES





(Concentration (mg/ml)





Compound

Molecular
Height

367

371

366

364

Comments

Naphthalene

128

4.2

4.6

6.8

0.34



Fluoranthene

202

1.3

4.2

2.9

0.075



Unknown

202

0.17

0.55

0.55

T



Pyrene

202

0.9

3.0

1.8

T



Chrysene
Triphenylene

228
228

0.3

1.2

0.8

0.028

Chrysene/T rlpheny-
lene unresolved

Unknown

228

0.007

0.09

0.1

T



Benz (a} anthracene

228

0.30

1.0

0.8

0.024



•Benzo (c) phenanthrene

228

0.044

0.14

0.18

T

RRT used for ID

Benzo (a) pyrene

252

0.24

0.7

0.65

0.02



Benzo (e) pyrene

252

0.12

0.3

0.38

0.01



Benzofluoranthene

252

0.47

1.7

1.2

0.043



Unknown

252

0.07

0.27

0.24

T



•Benz (j) aceanthrylene

252

.

-

-

-

No RRT to confirm

Perylene

252

0.14

0.17

0.27

ND



•7,12-Dlmethylbenz (a) anthracene

256

ND

ND

ND

ND

MS should be unique

Mbenzo (c, g) carbazole

267

NO

ND

ND

ND



*3-Methylcholanthrene

268

ND

ND

ND

ND

MS should be unique

Indeno (1,2, 3-cd) pyrene

276

0.10

0.22

0.42

T



Unknown

276

0.055

0.14

0.19

T



Unknown

276

0.01

0.055

0.05

ND



~Dlbenzo (a, h) anthracene

278

0.Q55

0.16

0.23

ND

Have 1, 2, 3, 4 and

*D1benzo (a, j) anthracene

278

0.055

0.80

0.12

ND

1» 2, 5, 6 Standards

Unknown

278

0.018

0.022

0.048

ND



•Dlbenz acrldlne

279

ND

«D

ND

ND

MS unique

•Olbenzo (a, h) pyrene

302

0.12
$









•Otbenzo (a, 1} pyrene

302

0.36

0.50

ND

Unresolved

•Standard not available (Identification based on published RRT and MS)
ND ¦ Not detected < 0.005 mg/ml
T • Trace < .01 Mg/ml but detected

$


-------
1W5.0-1

RECONSTRUCTED GC FROM 60 METER QV-17 GLASS CAPILLARY COLUMN
GC/MS (SAMPLE 367)

2252M.


-------




10^3H DRAFT

$>8-Of *-/J

SOURCE TEST AT U.S. STEEL
CLAIRTON COKE OVENS

CLAIRTON, PENNSYLVANIA

by

M. W. HARTMAN

Contract No. 68-02-2812
Assignment No. 13

EPA Technical Manager: Gene Riley

Prepared for:

Emission Standards and Engineering Division
Emission Measurements Branch
U. S. Environmental Protection Agency
Research Triangle Park, NC 27711

TRW

ENVIRONMENTAL ENGINEERING DIVISION
3200 E. Chapel Hill Rd./Nelson Hwy.

P.O. Box 13000
Research Triangle Park, NC 27709

rough draft


-------
ENVIRONMENTAL ENGINEERING DIVISION

k &

1423.TEE.80.046

August 15, 1980

Mr. J. £. McCarley
Emission Measurement Branch
ESED, Mail Drop 13
Research Triangle Park, NC 27711

O

/

L-^fX 1

Dear Mr. McCarley:	(J

Enclosed are four copies of the draft report from the source test

performed at U. S. Steels, Clairton, Pennsylvania Plant, under contract

number 68-02-2812 work assignment 23. A copy of this report has been

sent to Mr. Roy Neulicht of the Test Support Section for his review. If

there are any questions please do not hesitate to call me.

Sincerely,	r ,

Wus kA-t-	Foi^

"1	it ev\

Tony E,~Eggleston, Manager
Test and Evaluation

TEE/dej

Enclosures

cc: Roy Neulicht w/enclosures
Gene Riley
Linda Harmon

Progress Center

3200 £. Chapel Hill Fid, /Nelson Hwy.

P.O. Box 13000

Research Triangle Park, N.C. 27709 {919)541-9100


-------
SOURCE TEST AT U.S. STEEL
CLAIRTON COKE OVENS

CLAIRTON, PENNSYLVANIA

by

M. W. HARTMAN

Contract No. 68-02-2812
Assignment No. 23

EPA Technical Manager: Gene Riley

Prepared for:

U. S. Environmental Protection Age
Emission Standards and Engineering Divi
Emission Measurements Branch
Research Triangle Park, NC 27711

TRW Environmental Engineering Division
3200 E. Chapel Hill Rd./Nelson Hwy.
P. 0. Box 13000

Research Triangle Park, NC 27709



w A?.

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we*

~V







*c?r'



— €~


-------
PREPARATION OF BAP/POM AND BSO SAMPLES
CLAIRTON COKE WORKS

The attached schedule outlines the specific details of how each

sample collected at the Clairton Coke Works is to be prepared and

split for analysis. The schedule is detailed as follows:

I.	Splitting nozzle/vent samples.

II.	Combining nozzle/probe rinse samples for BAP.

III.BAP	sample preparation and splitting.

IV.	Combining BAP sample fractions.

V.	Re-extraction of filter and resin with cyclohexane.

VI.	Combining BSO probe/nozzle samples.

VII.Splitting	BSO sample fractions.

VIII.List	of samples to be sent to EPA for TLC analysis.

IX.	List of samples to be sent to EPA for transmittal to U.S. Steel Corp.

X.	List of samples for GC/MS analysis.

XI.	List of samples for BSO analysis.

XII.List	of samples to be retained for possible analysis at a future date.
Notes:

Prior to conducting this work run blank analysis on MeCL^cyclohexane,
and benzene to be used in laboratory to assure contamination is not present.

1.	Assure that splitting of the samples is done accurately to the
indicated fractions since split samples will be recombined before analysis
is conducted.

2.	Assure that samples are homogeneous prior to splitting. Use
ultrasonic agitation if necessary.


-------
3.	Prepare POM/BAP samples according to procedures outlined in
the draft test method for BAP except that methylene chloride shall be
used instead of cyclohexane (filter and solid resin extraction).

4.	Prepare and analyze BSO samples according to procedures
outlined in the draft test method for benzene soluble organics.

5.	Extract filter and resin according to procedures established
in the BAP method, paragraph 4.3, except that methylene chloride, in
lieu of cyclohexane, is to be used. Split the methylene chloride
extract; retain the filter and solid resin for re-extraction with
cyclohexane according to the procedures of paragraph 4.3 of the BAP
method.

6.	Extract the condensate according to the extraction procedures
of paragraph 4.3.3. of the BSO test method substituting cyclohexane
for benzene. (Do not filter or bring to dryness).

7.	Evaporate the sample to dryness and then redissolve the sample
residue*benzene. Combine this benzene solution as indicated.


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