United Stales
Environmental Protection
Agency
EPA-600/R-93-080 a
May 1993
<&EPA Research and
Development
KRESS INDIRECT DRY COOLING
S VST KM, BETHLEHEM STEEL'S
COKE PLANT DEMONSTRATION AT
:SPARROWS POINT, MARYLAND
Volume 1. Technical Report and
Appendices A~F
Prepared for
Office of Environmental Engineering
and Technology Demonstration
Prepared by
Air and Energy Engineering Research
Laboratory
Research Triangle Park NC 27711
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EPA REVIEW NOTICE
This report has been reviewed by the U.S. Environmental Protection Agency, and
approved for publication. Approval does not signify thai the contents necessarily
reflect the views and policy of the Agency, nor does mention of trade names or
commercial products constitute endorsement or recommendation for use.
This document is available to the public through the National Technical Informa-
tion Service, Springfield, Virginia 22161.
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- TECHNICAL REPORT DATA
, __ (Pkasc read Insmicrions on the rc.ene before vttrr.plet'
' . HtPCH I NO 2.
EPA-600/R-93-080 a
s PB93-19 130 2
& TITLS AND SUBTITLE
Kress Indirect Dry Cooling System, Bethlehem Steel's
Coke Plant Demonstration, at Sparrows Point, Mary-
land, VolT'1. Technical Report and Appendices A-F
5S RF.PORT DATE
May 1993
6. PERFORMING ORGANIZATION CODE
7. AUTHORISI
A. George Ossman
8. PERFORMING ORGANIZATION RfcPORT NO.
0. PERFORM NG OROANIZATION NAME AND ADDRESS
Bethlehem Steel Corporation
Bethlehem, Pennsylvania 18016-7699
10. PROGRAM ELEMENT NO.
11. CONTRACT/GRANT NO.
68-DC-0128
13, SPONSORING AfiFNCY NAME AND ADDRESS
EPA, Office of Research and Development
Air and Energy Engineering Research .Laboratory
Research Triangle Park, NC 27711
13. TYPE: Ol- RbPORT AND PfcHIOD COVERED
Final; 2/90 - 2/92
14. SPONSORING AGENCY CODE
EPA/600/13
15. supplementary notes ^EERT, project officer is Chester A. Vogel, Mail Drop 61, 919 '
541-2827. Volume 2 consists cf Appendices G-N.
23' The report evaluates the Kress Indirect Dry Cooling (KIDC) process, an
innovative system for handling and cooling coke produced from a slot-type by-product
coke oven battery. The report is based on the test work and demonstration of the sys-
tem at Bethlehem Steel Corporation's Sparrows Point (Maryland) facility in 1991. The
report covers .both environmental and operational impacts of the KIDC process.
Areas covered in the report.include opacity levels, quenching emissions, and the im-
pact of the KIDC coke on blast furnace operations. Also evaluated were various per-
formance characteristics of the KIDC system, including reliability, cycle time, coke
cooling requirements, and costs. Unfortunately, abbreviation of the test program,
caused by the idling of coke production at Sparrows Point, limited the experience
gained and data collected during the demonstration.-.. The report data have not been
thoroughly audited, and the conclusions are neither" approved nor endorsee by EPA.
Because of the sudden termination of the project/and the associated quality assurance
effort, it was not possible to perform the detailed laboratory and data audits that had
been planned. ' . , „ v.
17. KLY VYO H Jii ANL) UCCUMLNI AN A1 TI5
3. DESCRIPTORS
i). IDE NT! Fl ERS/OPE
N ENDED TERMS
c. COSATl Fiel.i/Citnu;?
Pollution
Coke
Coking
Blast Furnaces
Pollution Control
Stationary Sources
Kress Indirect Dry Cool-
ing (KIDC) Process
13 B
21D
13 H
1!F
-.3. OiS'PlisuTICN STATfcVfcNT
Release to Public
Unclassified ! 277
?0. SECURITY CLASS jThis page) <22. PR CE
Unclassified ;
EPA Fn'ii 2220-1 <9-73) F" 14
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EP A-600/'R-93-080 a
May 1993
KRESS INDIRECT DRY COOLING SYSTEM.
BETHLEHEM STEEL'S COKE PLANT DEMONSTRATION
AT
SPARROWS POINT, MARYLAND
Volume 1. Technical Report arid Appendices A-F
By:
A. George Ossman
Bethlehem Steel Corporation
Bethlehem, PA 18016-7699
EPA Contract No. 68-DO-0128
Project Officer: Chester A. Vogel
U.S. Environmental Protection Agency
Air and Energy Engineering Research Laboratory
Research triangle Park, NC 27711
Prepared For:
U.S. Environmental Protection Agency
Office of Research and Development
Washington. DC 20460
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APSTPACT
This report provides an evaluation of the Kress indirect Dry Cooling (KIDC) process.
The KIDC process is an innovative system tor the handling and cooling of coke produced from a
slot type by-product coke oven battery. The report is based on the test work and demonstration
of the system at Bethlehem Steel Corporation's Sparrows Point facility in 1991. The report
covers both environmental and operational impacts of the KIDC process. Areas covered in the
report include opacity levels, quenching emissions, and the impact of the KIDC coke on blast
furnace operations. Also evaluated were various performance characteristics of the KIDC
system. These included reliability, cycle time, coke cooling requirements, and costs.
Unfortunately, the shortened duration of the test program as a result of the idling of coke
production at Sparrows Point limited the experience and data collected during the demonstration.
DISCLAIMER
The data presented in this report have not been thoroughly audited and the conclusions
are not approved or endorsed by the Agency. Because of the sudden termination of the project
and the associated Quality Assurance effort, it was not possible to perform the detailed
laboratory and data audits that had been planned.
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TABLE OF CONTENTS
I.0 Introduction 1
I.1 Process Description 2
2.0 Conclusions 4
3.0 Test Program 5
3.1 Baseline Program 5
3.2 Demonstration Program 7
3.3 QA/QC Program 7
4.0 Test Program Results 18
4.1 Environmental Observations 18
4.2 KIDCi Box Gas Sampling 25
4.3 Area Monitoring 28
4.4 Quenching Emissions 29
5.0 Coke Quality & Yield 32
5.1 Coal Mix 32
5.2 Coke Quality 32
6.0 Impact of KIDC Coke on Blast Furnace Operations 36
7.0 KIDC Operating Costs 38
8.0 KIDC Boxes 39
8.1 Erosion/Corrosion of Steel Plates 39
8.2 Maintenance Observations 40
8.3 KIDC Water System Treatment 40
9.0 KIDC Reliability ,. 41
10.0 KIDC Cycle Time 42
II.0 Cooling Times 44
II.1 Three-Dimensional Heat Transfer Modeling 44
12.0 Capital Costs 47
12.1 Phase I Concept Costs 47
12.2 Phase II Concept Costs 48
13.0 Suggestions for Future Work 49
References 50
i i i
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APPENDICES
Page
A. Visible Emission Observation Data and Summary Tables - A-1
Pushing Emissions
B. Visible Emission Observation Data and Summary Tables - B-1
Pushside, Topside, and Discharge and Handling Emissions
C. Keystone Consulting Engineers Report on K1DC Box Gas Sampling C-1
D. Area Monitoring Data Sheets and Analytical Results D-1
E. Quench Tower Emissions and Water Analysis E-1
F Kress Bulletin and Photographs of the KIDC Operation F-1
G. Coke Quality Data G-1*
H. Blast Furnace Balwax Model Report H-1*
I. Report of KIDC Operating Costs and Maintenance Requirements 1-1*
J. Kress Box Thickness Readings J-1*
K. KIDC Coke Discharge Temperature K-1*
L. QA/QC Program L-1*
M. Door Leak Data M-1*
N. Coal Data N-T
'In Volume 2
IV
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FIGURES
Number Page
10-2 Average Time Between Push Comparison 43
11 -2 KIDC Coke Temperature vs. Cooling Time 46
v
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I&SLES
Number Page
3-1 Baseline and Demonstration Test Program Parameters 6
3-2 Conventional Pushing Emission Observation Quality
Assurance Data 9
3-3 KIDC Pushing Emission Observation Quality Assurance Data 10
3-4 Pushside Pushing Emission Quality Assurance Data
Conventional Pushing Emission Control 11
3-5 Topside Pushing Emission Quality Assurance Data
Conventional Pushing Emission Control 11
3-6 Discharge and Handling Emission Quality Assurance Data
Conventional Pushing Emission Control 12
3-7 Discharge and Handling Emission Quality Assurance Data
KIDC Pushing Emission Control 12
3-8 Door Observation Quality Assurance Data 13
3-9 Comparison of Coke Analysis by Laboratory 15
3-10 Conventional Pushing Coke Oven Area Sample QA 17
4-1 Comparison of Visible Emission Observations for Pushing
Emission Control Systems 21
4-2 Comparison of Topside Visible Emission Observations for
Pushing Emission Control Systems 22
4-3 Comparison of Pusherside Visible Emission Observations
for Pushing Emission Control Systems 22
4-4 Comparison of Visible Emission Observations for Coke
Discharge and Handling Operations 24
4-5 KIDC Box Sampling Targeted Compounds 26
4-6 Compounds Found in Identification Scan of KIDC Box Samples 27
vi
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Nutter
Paq?
4-7
GC/MS Identified Compounds from Conventional Coke Oven
Door Machine Area Samples
29
5-1
Comparison of KIDC Coke vs. Conventionally Quenched Coke
33
10-1
Cycle Times for the KIDC and Conventional Pushing Systems
42
11-1
KIDC Cooling Times and Discharge Temperatures
45
vii
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1.0 INTRODUCTION
On September 29,1990, Bethlehem Steei Corporation (Bethlehem) entered into a contract
with EPA to conduct a demonstration of a pollution control process that largely eliminates the
particulate emissions and water pollution normally associated with the uncontrolled pushing and
quenching operations inherent in the production of metallurgical coke. The demonstration was
to include the design, construction, operation, and evaluation of this system on one or more
commercial byproduct metallurgical coke oven batteries. The system chosen for this
demonstration was the Kress Indirect Dry Cooling (KIDC) system which controls both the pushing
and quenching emissions from coke production. Bethlehem provided as a host coke oven site.
Battery 11, at Sparrows Point, Maryland, with ancillary facilities as well as all equipment and labor
required to conduct this demonstration.
The successful application of the KIDC system to an existing coke oven battery(ies) was
expected to demonstrate that (a) almost all the particulate emissions normally associated with the
pushing operation are eliminated: (b) all of the particulate and the gaseous emissions associated
with the direct contact water quenching operation are eliminated; (c) this technology costs less
and is more effective than technologies that need to be combined to control pushing and
quenching emissions; (d) this technology produces a better grade coke with less raw coal usage
than alternative approaches; and (e) any problems resulting from this dry quenched coke as
produced by KIDC such as increased dustiness or adsorbed gas retention can be resolved in a
cost effective manner.
The KIDC system was selected by Bethlehem over other control alternatives for its potential
to supply superior control of pushing emissions, and at the same time, provide superior coke
quality at less operating costs, in addition, the elimination of quenching emissions was seen as
another potential environmental benefit to the KIDC system. The goal of the testing program was
to evaluate these factors to determine if the KIDC system is a viable and cost effective alternative
to other conventional control methods currently in use at other coke oven operations.
The KIDC Indirect Dry Cooling (KIDC) concept had been under development by the Kress
Corporation since the early 1980's. On June 6, 1987, the first prototype testing started at
National Steel Corporation's Granite City Division in Granite City, Illinois. During this testing 27
pushes were successfully taken by the KIDC system. In December 1988, the first demonstration
of the KIDC prototype occurred at the Bethlehem's Sparrows Point plant with the successful
demonstration of 12 pushes. Following this testing, Bethlehem signed a contract with the Kress
Corporation to install a full scale production system. The installation occurred in two phases.
Phase I was the installation and demonstration of the new technology on coke oven battery No.
11, and Phase II was an extension ol the system to include controls on battery No. 12.
The KIDC system was contracted to start testing in May, 1990, but delays prevented
start-up of the system until June 7, 1991. Start-up testing of the system continued for
approximately three and a half months until the start of the performance demonstration at the
beginning of October, 1991. This performance demonstration continued through October and was
extended into November, 1991.
1
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The demonstration test program originally called tor 30 weeks of testing consisting of; (1)
a Performance Test Program lasting about four weeks, and (2) an Operational Test Program
lasting about 26 weeks. However, on September 16, 1991, Bethlehem Steel announced that for
a variety of reasons, it was necessary to temporarily discontinue all coke making at the Sparrows
Point plant by the end of the 1991. As a result, all EPA related testing of the KIDC system was
concluded by the end of November. Overall the KIDC system accepted a total of 321 pushes
from June to the end of November and a total of 270 pushes during the two month performance
demonstration.
1,1 Process Description
1.1.1 The KIDC System
The KIDC system is a patented process of the Kress Corp. for the cooling of coke after
removal from a coke oven. It was designed to control emissions during both the pushing and
quenching operations. The KIDC process attempts to confine the emissions completely during
the push, unlike previous emission control technologies which typically rely on filtering or
scrubbing the emissions after they have escaped. The conventional pushing technologies used
for the baseline testing reported here utilized a water spray during the push to reduce particulate
emissions or a Chemico control car.
The KIDC system completely eliminates the wet quenching process and relies instead on
an indirect dry cooling process. The hot coke never comes into direct contact with the cooling
water, thus eliminating the vigorous evolution of steam and consequent entrainment of particulate
matter.
The KIDC carrier is an impressively large piece of equipment, weighing approximately
400,000 lbs (180,000 kg), with 8 ft (2.4 m) rubber tires. It is designed to carry and manipulate
one 50 ft (15.2 m) long, 13 ft (4 m) high, and 3 ft (0.9 m) wide KIDC container (box). It has two
dozen or more separate hydraulic cylinders to handle the intricate operations described below.
These hydraulic cylinders have computer/electronic sensors for exact positioning and control.
Auxiliary equipment includes 10 or more KIDC boxes, a support rail, a maintenance building, a
quench station, and a fueling station. The support rail is used to balance the carriers weight,
counteract pushing forces, and maintain the carrier at a precise distance from the oven. Other
functions of the KIDC Carrier include door removal/replacement, door and jamb cleaning, and the
catching of coke debris upon door handling.
The KIDC box, which is slightly wider and deeper than the coke charge, is positioned flush
against the coke oven and receives the push. The KIDC process utilizes the conventional push-
side apparatus. After the push Is completed and the pusher ram is withdrawn, the KIDC box's
guillotine door closes. The VOCs are controlled by a flare at the rear of the box, which is ignited
during the push or start of travel. During the pushing operation, the KIDC carrier is also designed
to clean the coke-side door and door jamb, which should facilitate the meeting of the proposed
NESHAP regulations on door leaks. The jamb cleaner was, however, not operable during the
demonstration. After the push, the box is transferred to the quenching station. During travel,
VOCs also evolve and burn through small leaks at the guillotine door. The carrier runs cooling
water on the outside of the box during the push and travel primarily to protect the box from
overheating.
2
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At the quench station, the carrier moves the box from the carrier into one of the nine
cooling racks. Cooling water runs over the box to cool the coke. A recirculation fan, which
derives power from a drive wheel in the quench rack, aids this cooling. During the first part of
the quenching process, VOCs still evolve and burn at the guillotine door. After cooling, the carrier
removes the box from the rack, carries it to the receiving station, where the guillotine door is
opened and the box is emptied by tilting.
Figures showing the carrier performing some of these operations are In Appendix F.
1.1.2 Coke Oven Battery Nos. 11 and 12
Battery Nos. 11 and 12 are underjet four meter batteries with 65 ovens each. These
batteries were constructed by Koppers and commissioned in 1955 and 1957 respectively. The
condition of the batteries had, however, deteriorated significantly with age. At the time that testing
began in 1991, a total of 22 ovens were in service on battery No. 11 with coking times which
ranged from 23 to 48 hours. In general, production on No. 11 battery was 18 ovens pushed per
day. This production was scheduled during two shifts, 11pm - 7am and 11am - 7pm. This was
done because of the small number of ovens available and to balance gas flows in order to obtain
a consistent coke oven operation.
3
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2,0 CONCLUSIONS
The report data have not been thoroughly audited, and the conclusions are neither
approved nor endorsed by the Environmental Protection Agency. Because of the sudden
termination of the project and the associated quality assurance effort, it was not possible to
perform the detailed laboratory and data audits that had been planned. The test program at
Sparrows Point did not demonstrate the long term viability of the KIDC system. The KIDC
system was not operated nearly long enough and did not take enough pushes to be able to state
with confidence that this system is or is not a reliable and an economically viable pushing
emission control system.
1. The test program at Sparrows Point demonstrated that the KIDC concept is technically
viable and (a) can lead to a significant reduction in emissions related to the coke pushing
and quenching operation, and (b) produce high quality coke with significantly less
moisture than wet quenched coke.
2. The KIDC system effectively controlled pushing emissions to a maximum average
opacity level of approximately 20% which was generally related to emissions from the
box flare stack before ignition. This represents a significant Improvement over the
conventional control systems utilized at sparrows Point to control pushing emissions.
The added benefit of the KIDC system is that it eliminated quench tower emissions.
This was somewhat offset by emissions during the box dumping procedure which
showed an increase over the conventional coke discharge operation.
3. Coke quality improvements were seen in the areas of coke moisture and stability. No
improvements could be substantiated in other coke quality characteristics such as an
increased size, lower Bethlehem reactivity, or improvements in CRI/CSR. It is felt,
however, that these characteristics were not adversely impacted by the KIDC system.
These characteristics could not, however, be directly compared to the conventional coke
produced because of differences in the coke handling systems before sampling.
4. The receiving station design adversely effected the size of the KIDC coke as a result of
the extended free fall of the coke into the hopper.
5. The door extractor performance was good. This along with the Geotronics spotting
system provided reliable operation which would minimize production delays and
prevent door damage which can occur if not performed property.
6. The automatic door cleaner worked well
It should be emphasized that the KIDC concept is in the early stages of development and
although it has had some successes and some failures in its demonstration at Sparrows Point it is
a concept which deserves further evaluation.
4
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3.0 TEST PROGRAM
The basis for carrying out this test program was the experimental and quality assurance
plans approved by the EPA in early 1991. The EPA Project Officer and AEERL Quality
Assurance Officer provided guidelines for preparing these plans during meeting with Bethlehem
Steel Corporation personnel.
As originally described in the test plan, the KIDC program consisted of (1) evaluation of the
operational impact of the KIDC system on the Coke Oven facilities and operations, and (2)
evaluating the impact of the KIDC system on pushing emissions, quenching emissions, top side
and door emissions, coke quality, blast furnace operations and general area air quality.
The demonstration test program was scheduled for a 30 week period which included a
Performance Test lasting four weeks and an Operational Test Program lasting an additional 26
weeks. The test program was cut short, however, as a result of the stopping of all coke oven
production at Sparrows Point at the beginning of December of 1991.
The first KIDC push occurred on June 7,1991 and was followed by a start-up program which
lasted until October 1, 1991. During this start-up period 51 pushes were accepted by the KIDC
system. On October 1, the performance demonstration was started and lasted through the end
of November. The performance demonstration consisted of 9 KIDC pushes per day which
represented approximately 50% of the total production on No. 11 battery at that time. This limited
performance demonstration was due to a one (1) shift operation of the KIDC equipment.
3.1 Baseline Program
The baseline program was designed to provide an understanding of where the existing
operations was with respect to a number of parameters which might change from the
implementation of the KIDC system. The baseline parameters to be measured were established
in the experimental and quality assurance plans approved by the EPA in early 1991. Some of
the parameters included as part of the baseline and demonstration test programs are presented
in Table 3.1.
Additional information on the test methods used to evaluate these parameters is given in the
original test plan.
5
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Table 3.1
BASELINE AND DEMONSTRATION TEST PROGRAM PARAMETERS
Coal Quality
Moisture
Bulk Density
Size Analysis
Volatile Matter
Fixed Carbon
Sulfur
Ash
Free Swelling Index
Coke Pushing, Travel and Handling Emissions
Visible Emission Observations (Methods 9 & 22)
Pushing Emissions - Cokeside
Pushing Emissions - Topside
Pushing Emissions - Pushside
Discharge & Handling
Video Tape Recordings
Door Emissions
Percent door leaks by EPA Method 109 equivalent
Coke Quality
Moisture
Volatile Matter
Sulfur
Ash
Fixed Carbon
Stability & Hardness
Drop Shatter Test
Coke Reactivity (Bethlehem)
Coke Reactivity Index (CRI)
Coke Strength after Reaction (CSR)
Quench & Make-up Water Analysis
Total Cyanide
Arsenic
Lead
Mercury
Calcium
Hardness
Total Suspended Solids
Total Dissolved Solids
Area Monitoring of Cokeside Machinery
Total Particulates
Benzene Soluble Fraction of Total Particulate
GC/MS - Volatile & Semi-volatile Scan
Blast Furnace Operations
Balwax Model
Sulfate pH
Chloride Temperature
Oil & Grease TCLP
Ammonia
Phenol
Sodium
Sulfide
6
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3.2 Demonstration Program
The Demonstration Program was designed to (1) evaluate the operational impact of the
KIDC system on the Coke Oven facilities and operations, (2) evaluate the impact of the KIDC
system on pushing emissions, quenching emissions, topside and door emissions, and general
area air quality, and (3) evaluate the impact of coke quality on blast furnace operations.
During the demonstration, the coke ovens were operated in a normal manner with the same
coal blends used during the baseline period leading up to the demonstration test.
The demonstration test was originally scheduled over a 30 week period and consisted of (1)
a Performance Test Program lasting about four weeks, and (2) an Operational Test Program
lasting about 26 weeks. This testing was, however, performed over a two month period because
of the cessation of coke making.
3.3 QA/QC Program
An EPA approved QA/QC plan was developed and implemented for this project to assure
the quality and validity of data acquired throughout the test program and to assist In the
interpretation of that data. This QA/QC program consisted of a number of parts which were each
designed to identify potential problem areas and to establish a means for follow-up. Some of the
key items included in this program are given as follows:
• A well defined organizational structure with a clear division of responsibilities for each
person. A copy of the organizational chart developed for this program is presented in
Appendix L.
• Both internal and external audits with a procedure for follow up and corrective action of
deficiencies. A copy of various internal audit reports performed at the plant during the
demonstration are provided in Appendix L.
• Monthly progress reports and updates on the project status. These reports included a
section for update of various QA/QC activities. These reports are also provided in
Appendix L.
• A number of procedures were utilized to test the accuracy and precision of various
analytical methods and other testing procedures utilized throughout the project. These
procedures included multiple runs on the same sample, spiked samples, and
simultaneous side-by-side samples.
3.3.1 Quality Assurance of Visible Emission Observation (VEO) Data
All VEOs were performed by BCM Engineers, Inc. under a contract with Bethlehem.
Observers were trained and certified in emission observation techniques as required by EPA
Method 9. Copies of these certifications are provided in Appendix L.
7
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EPA Method 9 was utilized for the determination of the maximum opacity during the push
and EPA Method 22 was utilized for the determination of the total duration of visible emissions.
These methods were utilized for observation from the cokeside, the topside, and the pusherslde
of the battery during the pushing operation. In addition, observation of the coke discharge and
handling emissions were made from both the conventional and KIDC systems. Readings were
performed in a similar manner for both the conventional pushing operation and the KIDC system.
Cokeside observations for the KIDC system were, however, more specific so that emissions could
be evaluated based on the different operations and areas from which emissions occur in the
system.
Observation of door leakage was performed in accordance with the state of Maryland door
observation procedure. This method is very similar to the EPA proposed Method 109. The state
method differs from the EPA Method in that jamb leaks are excluded from the percent leaking
door calculation, and three doors (cokeside. pushside. and chuck) are counted per oven.
Some of the problems encountered in making the cokeside observations included steam
interference from the dust suppression sprays on the Shenango conventional control car and the
scrubber control on the Chemico control car. Steam Interference was less of a problem when
performing observations on the KIDC system, but steam from the water cooling sprays on the box
did at times interfere with readings at the box to jamb interface. The observers were aware of
these interferences and compensated by making observations after the steam had dissipated or
in areas of the plume where steam was not evident.
Problems were also encountered in following precisely the requirement of Method 9 which
calls for the sun angle to be within a 140 degree sector behind the observer. This was
unavoidable due to the orientation of the battery in an east to west direction with the cokeside
yard north of the battery. The observers were aware of this problem, however, and positioned
themselves in a way which minimized the impact from sun angle.
Multiple observer side-by-side readings were performed at each of the different areas ol
observation. Table 3-2 presents pushing emission data from three observers performing
simultaneous readings of the conventional pushing operation. These readings were made from
the cokeside yard on the north side of the battery. Table 3-3 presents similar data from
observation of the KIDC system during the push and travel operation. Tables 3-4 and 3-5 present
multiple observer data from the pushside and topside of the batteries respectively. These
readings were obtained during the conventional pushing operation. Tables 3-6 and 3-7 present
multiple observer data for the conventional and KIDC discharge and handling emissions
respectively. Table 3-8 presents multiple observer data of door observations. All of this data
shows good agreement between observers.
3.3.2 Quality Assurance of Quench Water Analysis
A report of the results of spiked samples and multiple runs on the same sample is provided
in the Monthly Progress Reports in Appendix L. This report shows good accuracy and precision
of the analytical methods utilized to determine the constituents in these waters. Spikes were not
run for total dissolved solids (TDS), total suspended solids (TSS), or oil/grease since appropriate
standards are generally unavailable for the spike procedure.
Except as noted in the two following paragraphs, sampling was performed in accordance
with the procedures set forth in the original sampling and testing plan dated January 10,1991 and
revisions to that plan dated March 28,1991. Sample preparation was performed according to the
methods described in EPA publication SW 846.
8
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TABLE 3-2
CONVENTIONAL PUSHING EMISSION OBSERVATION QUALITY ASSURANCE DATA
11/29/91 - Shenango Control Car
OPACITY
Max. ! Max.
Opacity | Opacity
During | During
Push | Travel
% | %
OVEN NO.
OBSERVER 1
OBSERVER 2
OBSERVER 3
AVERAGE
1151
85/50
80/45
75/45
80.0/46.7
1135
100/65
100/60
100/65
100/63.3
1153
50/35
50/30
55/30
51.7/31.7
1222
85/100
85/100
80/100
83.3/100
1232
35/0
30/0
30/0
31.7/0.0
AVERAGE
71.0/50.0
69.0/47.0
68.0/48.0
69.3/48.3
CUMULATIVE TIME OF EMISSIONS
Seconds | Seconds
During | During
Push | Travel
OVEN NO.
OBSERVER 1
OBSERVER 2
OBSERVER 3
AVERAGE
1151
107/105
107/105
105/107
106.3/105.7
1135
60/90
65/85
67/88
64.0/87.7
1153
59/35
60/30
71/48
63.3/37.7
1222
103/52
103/52
89/52
98.3/52.0
1232
41/0
41/0
43/0
41.7/0
AVERAGE
74.0/56.4
75.2/54.4
75.0/59.0
74.7/56.6
9
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TABLE 3-3
KIDC PUSHING EMISSION OBSERVATION QUALITY ASSURANCE DATA
11/25/91
OPACITY
Max. ( Max. | Max.
Stack [ Stack | Opacity
Opacity j Opacity | Box/Jamb
Before I After | Interface
Ignition ; Ignition |
OVEN NO.
OBSERVER 1
OBSERVER 2
OBSERVER 3
AVERAGE
1148
25/5/25
20/10/25
25/5/20
23.3/6.7/23.3
1151"
40/-/-
40/-/-
40/-/-
40/--/--
1153
20/10/10
15/10/10
10/10/15
15/10/11.7
1149
15/5/5
10/10/10
15/5/10
13.3/6.7/8.3
1172
20/10/10
15/15/10
15/10/10
16.7/11.7/10
AVERAGE
24/7.5/12.5
20/11.2/13.8
21/7.5/13.8
21.7/8.8/13.3
CUMULATIVE TIME OF EMISSIONS
Seconds | Seconds
During | During
Push | Travel
OVEN NO.
OBSERVER 1
OBSERVER 2
OBSERVER 3
AVERAGE
1148
60/40
66/43
67/40
64.3/41
1151
71/203
75/200
74/200
73.3/201
1153
107/85
110/85
109/83
108.7/84.3
1149
108/149
79/152
90/150
92.3/150.3
1172
91/165
83/175
90/170
88/170
AVERAGE
87.4/128.4
82.6/131
86/128.6
85.3/129.33
* Note: On push 1151, no ignition of the stack occurred and steam
interference prevented readings at the box/jamb interface.
10
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TABLE 3-4
PUSHSIDE PUSHING EMISSION QUALITY ASSURANCE DATA
CONVENTIONAL PUSHING EMISSION CONTROL - 7/29/91
Cum. | Max.
Time of , Opacity
Emissions : %
OVEN NO.
OBSERVER 1
OBSERVER 2
OBSERVER 3
AVERAGE
1242
20/20
20/25
20/25
20.0/23.3
1262
24/65
20/55
20/55
21.3/58.3
1272
124/30
122/30
122/30
122.7/30.0
1168
37/40
40/45
40/45
39.0/43.3
1214
105/60
110/50
110/50
108.3/53.3
AVERAGE
62.0/43.0
62.4/41.0
62.4/41.0
62.3/41.7
TABLE 3-5
TOPSIDE PUSHING EMISSION QUALITY ASSURANCE DATA
CONVENTIONAL PUSHING EMISSION CONTROL - 7/31/91
Cum. | Max.
Time of I Opacity
Emissions j %
OVEN NO.
OBSERVER 1
OBSERVER 2
OBSERVER 3
AVERAGE
1222
50/95
52/90
52/90
51.3/91.7
1232
35/15
46/15
45/15
42.0/15.0
1242
42/15
20/45
40/20
34.0/28.7
1262
27/15
22/15
25/15
24.7/15.0
1272
58/15
55/20
58/15
57.0/16.7
AVERAGE
42.4/31.0
39.0/37.0
44.0/31.0
41.8/33.0
11
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TABLE 3-6
DISCHARGE AND HANDLING EMISSION QUALITY ASSURANCE DATA
CONVENTIONAL PUSHING EMISSION CONTROL - 7/29/91
Curn. | Max.
Time of | Opacity
Emissions ; %
TIME
OBSERVER 1
OBSERVER 2
OBSERVER 3
AVERAGE
11:54am
10/8
10/10
7/10
9.0/9.3
12:04
10/5
10/5
8/5
9.3/5.0
12:32
0/0
0/0
0/0
0.0/0.0
12:50
0/0
0/0
0/0
0.0/0.0
13:09
22/5
22/5
11/15
18.3/8.3
AVERAGE
8.4/3.6
8.4/4.0
5.2/6.0
7.3/4.5
TABLE 3-7
DISCHARGE AND HANDLING EMISSION QUALITY ASSURANCE DATA
KIDC PUSHING EMISSION CONTROL - 11/25/91
TIME
12:55pm
13:51
14:13
AVERAGE
OBSERVER 1
23/5
11/5
5/5
13.0/5.0
Cum. | Max.
Time of i Opacity
Emissions j %
OBSERVER 2
20/5
15/5
0/0
11.7/3.3
OBSERVER 3
25/5
15/5
0/0
13.3/3.3
AVERAGE
22.7/5.0
13.7/5.0
1.7/1.7
12.7/3.9
12
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TABLE 3-8
DOOR OBSERVATION QUALITY ASSURANCE DATA
AUGUST 1. 1991
Door Type
Battery No. 11
Pushside
Cokeside
Chuck
Battery No. 12
NUMBER OF DOOR LEAKS OBSERVED
Observer 1 Observer 2 Observer 3
10
9
4
9
10
3
10
9
3
Average
9.7
9.3
3.3
Pushside
Cokeside
Chuck
Total
5
14
1
43
5
15
1
43
5
15
1
43
5.0
14.7
1.0
43
13
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Modifications to the original test plan occurred in a number of areas. The first was a change
in the sampling location of the quench waters. The original sampling plan called for samples to
be obtained of the return water to the quench pit following the quench. This was changed on
August 29,1991 to the water feed to the quench sprays during quench. In addition, a change was
made to the analytical procedure for TDS analysis on October 4. This change involved running
the analysis at 103-105CF vs. 180°C. These changes were made following the recommendations
of J. Jeffery of Alliance Corp. (See report in Appendix E).
The number of samples obtained was reduced due to the shortened duration of the testing
program. In addition, water samples from the KIDC recirculated water system were not obtained
so that efforts could be focused on other testing activities. The make-up water to this system was
sampled on three occasions, however, to ensure that its quality was essentially the same as that
used in the conventional quenching process.
3.3.3 Quality Assurance of Coke Quality Data
All of the coke physical and proximate testing was performed in accordance with the ASTM
standards provided in the original sampling and testing program. This testing was performed by
the Sparrows Point Plant Laboratory. The testing of Coke Reactivity Index (CRI) and Coke
Strength after Reaction (CSR) was performed by Hampton Roads Testing Lab. Sampling
followed the plant key variable standard operating procedures (KVSOP) provided in the original
test plan.
Additional samples were submitted to Consol Coal Company In Library, PA. The purpose
of this testing was to assure that the physical and chemical test results obtained at the Sparrows
Point Laboratory were repeatable and accurate when compared to another facility. The results
of this testing are presented in Appendix G. Table 3-9 presents a comparison of Consol Coal
Company test results with results obtained from the Sparrows Point Laboratory during the same
time period. It should be noted that these are not split samples and would therefore, include
variability from different samples and possibly different ovens.
Physical differences observed between the two coke populations could be partially due to
differences in the matenal handling systems. The KIDC coke was discharged into a receive
station which was designed to handle higher production levels than were experienced during the
demonstration. As a result, the KIDC coke experienced a free full of approximately 30 ft. Other
differences such as the collection of breeze (i.e., - Vz") by the KIDC system which are not
normally collected or are washed out in the conventional pushing and quenching operation may
have also affected the results of the data obtained.
14
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TABLE 3-9
COMPARISON OF COKE ANALYSIS BY 1 ABORATORY
CONVENTIONAL COKE
Laboratory
Sparrows Poinl
Ave. of 2 Analyses
10/28/91
Hampton Roads
Ave. of 2 Analyses
10/27 & 10/29
Consol Coal
One Analysis
10/28/91
Absolute Difference
Volatile
Moisture Matter Ash S Stability Hardness CRI CSR
1.67
7.2
0.65 8.15 0.56 60.0
5.53 0.41 0.59 0.01
0.0
68.6
24.9 63.0
1 06 8.74 0 57 60.0 67.2 29.3 52.4
1.4
4.4 10.6
KIDC COKE
Laboratory
Sparrows Point
Ave. ol 2 Analyses
10/29/91
Hampton Roads
Ave. of 2 Analyses
10/29/91
Consol Coal
Ave. of 5 Analyses
10/28 & 10/29
Volatile
Moisture Matter Ash S Stability Hardness CRI CSR
0.52
0.5
0.37 8.03 0.55 64.0
69.2
25.0 63.8
1.10 8.90 0.58 63.1 68.6 25.9 62.0
Absolute Difference
0.02 0.73 0.87 0.03
0.9
0.6
0.9 1.8
15
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3.3.4 Quality Assurance of Area Monitoring
Area Monitoring was performed to determine the concentrations of a number of air
contaminants in the area around the cokeslde bench of the coke ovens. This sampling was
performed by industrial hygiene methods over eight hour periods.
In order to evaluate the accuracy and precision of these methods, side-by-side samples were
obtained on four occasions to evaluate the variability of the results during the same time period.
The results of these side-by-side tests are presented in Table 3-10 and show a high degree of
variability. Samples were also obtained at some distance upwind of the coke ovens in order to
determine to what extent ambient levels of the air contaminants might effect the results obtained
at the coke oven operation. The results of this testing are given In Appendix D and show that
ambient levels of particulates and Benzene Soluble Organics (BSO) are below the detection limits
of the method used. All laboratory analyses were performed by American Medical Laboratories,
Inc. Documentation on their quality assurance program is included in Appendix L.
A GC/MS identification scan was performed on three (3) samples. These samples were
obtained by adsorption onto Carbotrap 300 tubes over periods of 5, 10, and 15 minutes. These
samples were obtained side-by-side with the same starting time. The pump utilized for sampling
was calibrated just prior to use to give a sampling rate of 175 ml/min. The GC/MS used for the
analysis of the samples is calibrated daily by American Medical Laboratories, Inc. The calibration
is performed using the GC/MS autotune function and a perflourotributylamine standard.
3.3.5 Quality Assurance of Kress Box Gas Sampling
A report and description of the QA/QC procedures utilized by Keystone Environmental
Resources, Inc. in the performance of the Kress box sampling is included in Appendix L. Some
of the procedures utilized included:
• Sorbent Traps in Series
• Field Blanks
• Surrogates Added to Extracts
• A schedule for Concurrent Calibration
16
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TABLE 3-10
CONVENTIONAL PUSHING COKE OVEN AREA SAMPLE QA
DATE TOTAL PARTICULATE MATTER BENZENE SOLUBLE ORGANICS
(MG/M3) (MG/M3)
5/13/91 13.90 5.44
5/13/91 8.22 5.00
Difference 5.68 0.44
7/31/91 22.35 1.10
7/31/91 16.66 0.84
Difference 5.69 0.26
8/01/91 7.64 1.28
8/01/91 3.76 1.67
Difference 3.88 0.39
9/13/91 5.68 0.90
9/13/91 8.23 1.11
Difference 2.55 0.21
Average Cone. 10.80 2.17
Ave. Difference 4.45 0.32
17
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4.0 TEST PROGRAM RESULTS
4.1 Environmental Observations
Visible emission observations (VEO) were performed to compare the emission levels during
the pushing operation of the KIDC system versus the conventional pushing systems. The VEO
readings were performed in accordance with EPA Method 9 to determine the maximum opacity
dunng the push and in accordance with EPA Method 22 to determine the total duration of visible
emissions. All observers were properly trained and certified in opacity readings by Method 9.
These observations were performed from three locations: the cokeside yard, the topside of the
battery, and the pusherside of the battery. A summary table of the results of all VEOs performed
as part of this demonstration is given in Appendix A and B. In addition to the VEOs, video tapes
of conventional and KIDC pushes were recorded as described in the original test plan for EPA.
Copies of these video tapes have been provided to EPA under a separate cover.
4.1.1 Cokeside Pushing Emission Observations
Summary tables presented in Appendix A show the averages and standard deviations of
opacity readings performed for Doth the conventional pushing operation and the KIDC system.
As shown, these data indicate a substantial reduction in visible emissions with the KIDC vs. the
conventional controls typically utilized by Sparrows Point.
The observations from the cokeside yard were initiated at the movement of the coke mass
and ended with the start of the quenching cycle or for the KIDC system with the placement of the
box into the cooling rack. Emissions which may have resulted from removal of the door and
before the movement of the coke mass were not observed as they were uncontrolled for both the
conventional and the KIDC systems.
In many cases, the readings from the coke side yard did not conform precisely to the
requirement of EPA Method 9 which calls for the sun angle to be within a 140° sector behind the
observer. This was unavoidable because of the orientation of the batteries In the east to west
direction with the coke side yard on the north side of the battery. The observers were aware of
this problem, however, and positioned themselves in a way which minimized the impact from sun
angle. This problem existed for both the conventional and KIDC observations so any bias in the
readings from sun angle would be reflected in both sets of readings. Valid comparisons between
the two sets of readings can therefore be made. In addition, the considerable amount of steam
generated during the conventional pushing operation from the dust suppression sprays on the
Shenango control car made opacity readings difficult at times. The opacity readers were aware
of this problem and attempted to perform readings either after the steam dissipated or in areas
where steam was not evident.
Steam interference was less of a problem with the KIDC system, but readings at the box to
jamb interface were difficult at times due to steam from the non-contact cooling water cascading
over the box surface.
As a result of the condition of Battery No. 11 during the demonstration many of the pushes
observed would be considered "green". This means that portions of the coke were not fully
carbonized and resulted in coke from certain areas of the oven (eg. the ends) being higher In
volatile matter than is sometimes achieved. This may have resulted in higher opacity readings
for both the conventional and KIDC pushing operations than would be expected from "non-green"
pushes.
18
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4.1.1.1 Conventional Control System
The VEO data for the conventional systems show a maximum average opacity of 69 percent
overall during the push and 32.1 percent overall during travel with standard deviations of 28.7 and
24.4 respectively. The cumulative time of visible emissions for the conventional systems shows
an average of 71.6 sec. during pushing and 46.9 sec. during travel to the quench tower.
4.1.1.2 KIDC System
The VEO readings of the KIDC system show emissions from the box flare stack both before
and after ignition and at the box to jamb interface. The overall maximum average opacity levels
for these areas were 20.4,12.2. and 9.1 percent respectively. The standard deviation of these
emission levels are 10.6, 6.9, and 5.9 percent respectively. The cumulative time of emissions
indicates an average of 72.1 seconds during the pushing cycle and 120.6 seconds during the
travel cycle. The longer cumulative time of emissions during travel for the KIDC system vs. the
conventional system does not necessarily indicate an increase in the total particulate emissions
for the KIDC system because of the significantly reduced magnitude of the emissions. The longer
emission time is primarily due to long travel times caused by low carrier speeds during the
demonstration. Significant increases in travel speed projected by Kress Corporation for future
testing would reduce these emissions. Table 4-1 shows a comparison of the average VEO
results for the conventional and KIDC pushing emission control systems. A Student T-test
comparison of the maximum opacity during the push for the conventional system vs. the
maximum opacity from the KIDC flare stack before ignition shows that emission levels from the
KIDC system are statistically less. The results of this T-test analysis can be found in Appendix
A.
After ignition of the flare stack and during travel to the coke receiver station, there are visible
emissions from the flare stack on the KIDC box. These emissions averaged 12.2%. While these
emissions are not directly comparable, they are substantially less than the average maximum
opacity of travel emissions from the conventional systems of 32.1%. Student T-test results
provided in Appendix A show the difference between these emission levels to be statistically
significant.
Burning was often noted from seals at the box door. This burning often continued for an
hour or so while the box was in the cooling rack. This burning was not, however, a source of
visible emissions.
4.1.1.3 Relative Mass of Pushing Emissions
The KIDC system clearly produces substantially less emissions than the conventional
systems. It was not possible to quantify the total mass of the pushing emissions, but as shown
on the video tapes the mass of the emissions from the KIDC system was substantially less than
that of the conventional pushing emission control systems observed.
Pushing emission increases from the topside and pushside of the battery from the use of the
KIDC system are minimal when compared with the large reduction In cokeside emissions. In
addition, the elimination of quenching emissions from the use of the KIDC system clearly offsets
any increase in emissions from discharge and handling. Overall, the KIDC system substantially
reduced emissions versus the conventional controls typically used on Sparrows Point No. 11 and
12 batteries.
19
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4.1.2 Topside Observations
The topside VEO readings concentrated on emissions which emanated from charging ports
and standpipes as a result of the movement of the coke mass through the oven on pushing. The
inherent sun angle problem with the cokeside readings was not a problem for the topside
readings. Table 4-2 summarizes the average data for these observations.
These data show that both the conventional and the KIDC systems result in considerable
visible emissions from the topside of the battery. The average maximum opacity levels for the
conventional systems were 48.3% and 43.6% for the Shenango and Chemico control cars
respectively. The KIDC system had an average maximum opacity level of 80.5%. These
differences are statistically different when a Student T-test is applied at a 99% confidence level.
The conventional reading included observations from both No. 11 and No. 12 batteries which
when analyzed by battery show no statistical difference. The results of these T-test analyses can
be found in Appendix B.
The cumulative time of visible emissions from the topside averaged 51.8 seconds and 54.2
seconds for the Shenango and Chemico control cars respectively. The cumulative time of visible
emissions from the topside for the KIDC system averaged 73.0 seconds.
4.1.3 Pusherside Emissions
The pusherside VEO readings concentrated on emissions which emanated from the door
area of the oven being pushed as the pusher ram was extended into the oven and withdrawn.
These readings were performed in accordance with methods 9 and 22. Generally, no problems
were noted in following these methods with regard to sun angle or steam interference. Table 4-3
shows the average results of these observations.
VEO levels in this area appear to be somewhat higher for the KIDC systems versus the
conventional pushing operation. The average maximum opacities observed for the conventional
systems were 53.0% and 45.1% for the Shenango and Chemico control cars respectively. The
KIDC system had an average maximum opacity level of 61.9%. This shows a statistical
difference between the conventional and KIDC systems when a Student T-test is applied at a
99% confidence level. The conventional readings include observations from both 11 and 12
batteries. An analysis of these readings by battery show average maximum opacity levels of
52.8% and 50.7% for No. 11 and No. 12 batteries respectively. This indicates no statistical
difference between the readings on the two batteries when a T-test is applied. The results of
these T-test analyses can be found in Appendix B.
20
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TABLE 4-1
COMPARISON OF VISIBLE EMISSION OBSERVATIONS FOR
PUSHING EMISSION CONTROL SYSTEMS
(Average Readings)
Operation
Shenanao Car Chemico Car
KIDC
Pushing - Ave. Max. % Opacity
Jamb Interface
Flare Stack
Before Ignition
After Ignition and Travel
69.5%
NA
NA
NA
67.6%
NA
NA
NA
NA
9.1%
20.4%
12.2%
Travel - Ave. Max. % Opacity
33.1%
29.0%
NA
Cumulative Time of Emissions-sec.
Pushing
Travel
74.7
46.7
61.9
47.5
72.1
120.6
Relative Quantity of Emissions
(Engineering Judgement)*
Large
Large
Small
NA - Not Applicable
* Observation of video tapes will provide the reader with a better
comparison of the relative magnitude of the quality ot emissions
released by the respective pushing emission control systems.
21
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TABLE 4-2
COMPARISON OF TOPSIDE VISIBLE EMISSION OBSERVATIONS FOR*
PUSHING EMISSION CONTROL SYSTEMS
(Average Readings)
Operation Shenanqo Car Chemico Car KIDC
Pushing • Ave. Max. % Opacity 48.3% 43.6% 80.5%
Cumulative Time of Emissions-sec. 51.8 54.2 73.0
TABLE 4-3
COMPARISON OF PUSHERSIDE VISIBLE EMISSION OBSERVATIONS FOR*
PUSHING EMISSION CONTROL SYSTEMS
(Average Readings)
Operation Shenanqo Car Chemico Car KIDC
Pushing - Ave. Max. % Opacity 53.0% 45.1% 61.9%
Cumulative Time of Emissions-sec. 57.3 57.7 59.0
' Note: These emissions are small compared to conventional
controlled cokeside emissions.
-------
The average cumulative times of emissions for the conventional systems were 57.3 seconds
and 57.7 seconds for the Shenango and Chemico control cars respectively. The KIDC system
had an average cumulative time of emissions of 59.0 seconds. This shows no statistical
difference between the conventional and KIDC systems when a Student T-test is applied at a
99% confidence level. The conventional reading included observations from both No. 11 and No.
12 batteries. An analysis of these readings by battery shows an average cumulative time of
emissions of 58.2 seconds and 56.9 seconds for No. 11 and No. 12 batteries respectively. This
indicates no statistical difference between the readings on the two batteries. The results of these
T-test analyses can be found in Appendix B.
4.1.4 Discharge Emissions
VEO readings of the coke discharge and handling operation were recorded for both the
conventional and KIDC systems. All reading were performed in accordance with EPA Methods
9 and 22. In some instances, the observers were unable to locate themselves so that the sun
was in the required location at their back, and steam interference made readings of these
emissions difficult at times. The observers were aware of these difficulties, however, and
attempted to minimize these effects. Table 4-4 shows the average results of these observations.
The average maximum opacity of emissions for the conventional systems were 2.4% and
0.0% for October and November respectively. The KIDC system had an average maximum
opacity level of 15.7% and 9.0% for October and November respectively. These readings indicate
somewhat higher emission levels for the KIDC system vs. the conventional system. The overall
average maximum opacity for the conventional system on discharge to the wharf was 1.6%. This
compares to an overall average maximum opacity for the KIDC system of 13.1%. These
differences are statistically different when a Student T-test is applied at a 99% confidence level.
The results of this T-test analysis can be found in Appendix B.
The average cumulative time of emissions for the conventional systems was 4.5 seconds
and 0.0 seconds for October and November respectively. The KIDC system had an average
cumulative time of emissions of 66.5 seconds and 29.2 seconds for October and November
respectively. These readings indicate an increase in the duration of emissions for the KIDC
system vs. the conventional.
These readings indicate that the emissions levels for the discharge of coke for the
conventional pushing operation were minor. For the KIDC system, however, these emissions
were significant at times. Although a water curtain is used to suppress emissions from this
operation, other factors such as the temperature of the coke in the box can significantly affect the
performance of this system. When coke at a measured temperature of greater than 500°F is
discharged into the receiving station, water sprays are triggered to cool the coke. This
temperature is measured by two Ircon temperature sensors mounted after the coke receiving
hopper (see Section 11.0). These sensors were calibrated by the manufacturer on
October 2, 1992. A report of this calibration is included in Appendix K. This is done to protect
the hopper and the transfer belts from too high a temperature. The discharge of cool coke into
the receiving station could result in significantly reduced emission levels from this operation.
23
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TABLE 4-4
COMPARISON OF VISIBLE EMISSION OBSERVATIONS FOR
COKE DISCHARGE AND HANDLING OPERATIONS
Conventional
KIDC
Ave. Max. % Opacity
October
November
2.4%
0.0%
15.7%
9.0%
Cumulative Time of Emissions - sec.
November
October
4.5
0.0
66.5
29.2
* Note: These emissions are small compared to conventional controlled
cokes id e emissions.
4.1.5 Door Emissions
Daily monitoring of coke oven doors emissions were conducted on battery No. 11 throughout
1991. These observations were conducted in accordance with the state of Maryland door
observation procedure. This procedure is very similar to the EPA proposed Method 109. The
state method differs from the EPA method in that jamb leaks are excluded from the percent
leaking door calculations, and three doors (cokeslde, pushside, and chuck) are counted per oven.
The original reasoning for including this type of information as part of the initial sampling and
testing program for the KIDC project was to evaluate any impacts on door emissions which might
have resulted from the change in operation. The changes which might have been anticipated
could have resulted from a number of factors as follows:
~ Jamb damage from the pressing of the KIDC box against the jamb.
• Door damage from improper spotting or handling in the extraction or replacement
• Improved door performance from operation of the automatic door and jamb cleaners.
The KIDC door extractor removed and cleaned a total of 139 doors during the
demonstration. The KIDC jamb cleaner was not operational during the demonstration. The short
duration of the testing period along with the limited number of pushes taken by the KIDC system
during the demonstration prevented any reasonable conclusion from being made with respect to
the impact of the KIDC system on door performance. These data have been included for Battery
Nos. 11 and 12 for all of 1991 in Appendix M.
process.
24
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4.2 KIDC Box Gas Sampling
Sampling and analysis of the gases contained within a KIDC box was performed by
Keystone Environmental Resources, Inc. on October 30, 1991. The purpose of this testing was
lo provide both a qualitative and quantitative analysis of the gases which are held within the KIDC
box at the start and the end of the cooling cycle. Analysis for a number of volatile and
semi-volatile compounds were performed including a library scan to identify the most prominent
components. Three tests were performed during two cooling cycles. The sampling took place
at five minutes and at two hours into the cooling cycle. A report from Keystone Environmental
Resources, Inc. which details the methods and results of this testing is provided in Appendix C.
The results of these analyses show that volatile organic compound (VOC) concentrations
are extremely low for the gases held within the box. The semi-volatile compounds (SVOCs)
Investigated included three groups: polynuclear aromatic hydrocarbons (PAHs); phenols and
cresols; and phthalates. Many of the targeted PAHs were found above the detection level but at
very low levels. The analysis for phenols and cresols indicated the presence of two out of the
six targeted compounds. None of the targeted phthalate compounds were found above detection
levels. Table 4-5 presents a list of all of the targeted compounds with an indication of those
compounds found in concentrations equal to or greater than the detection level in at least one of
the three tests. In addition to the analysis performed for the specific targeted compounds,
identification scans were run to determine the presence of other compounds. A listing of the
compounds found from these scans is presented in Table 4-6.
The coke produced on No. 11 battery during this testing although generally of good quality
by industry standards for blast furnace performance would have been considered "green". This
means that portions of the coke were not fully carbonized and resulted in coke from certain areas
of the oven (e.g. the ends) being higher in volatile matter than is sometimes achieved. The VOC
and SVOC levels found in this testing would, therefore, be higher than what would be expected
from a typical push of non-green coke. In addition, the burning which occurs during the
conventional pushing operation until the start of quench destructs many of these constituents as
they are evolved. These results should, therefore, not be taken as an indication of VOC and
SVOC emissions from a conventional pushing operation.
The KIDC system incorporates a flare which ignites emissions from the box as it receives
coke from the oven and during travel to the cooling station. Once the box is placed in the cooling
station, the flare stack is closed off and gases are contained within the box. The VOC and
SVOC's would, therefore, not be emitted from the KIDC system at the levels measured during the
testing.
25
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TABLE 4-5
KIDC BOX SAMPLING TARGETED COMPOUNDS
Volatile Oraanic Compounds
Acryionitrile - ND
* Benzene
Chloroform - ND
* 2,4-Dinitrotoluene
2,6-Dinitrotoluene - ND
* Ethyl Benzene
Isophorone - ND
Styrene - ND
Toluene - ND
* m/p-Xylene
o-Xylene - ND
Semi-Volatile Organic Compounds
(Phenols and Cresols)
* 2,4-Dimethylphenol
4,6-Dinitro-o-Cresol - ND
Parachiorometacresol - ND
Pentachlorophenol - ND
* Phenol
2,4,6-Trichlorophenol - ND
Semi-Volatile Organic Compounds
(Polynuclear Aromatic Hydrocarbons)
* Acenaphthene
* Acenaphthylene
* Anthracene
* Benzo(a)anthracene
* Benzo(a)pyrene
* Benzo(b)tluoranthene
* Benzo(k)fluoranthene
* Benzo(g,h,i)perylene
' Carbazole
" Chrysene
* Dibenzo(a,h)anthracene
' Fluoranthene
* Fluorene
* lndeno(1,2,3-c,d)pyrene
* Naphthalene
" Phenanthrene
* Pyrene
Semi-Volatile Organic Compounds
iPhthalates)
Bis(2-ethylhexyl)phthalate - ND
Butyl Benzyl Phthalate - ND
Di-n-Butyl Phthalate - ND
Di-n-Octyl-Phthalate - ND
Diethyl Phthalate - ND
Dimethyl Phthalate - ND
* Compounds found at/or above detection levels in at least one test.
ND - Not detected
26
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TABLE 4-6
COMPOUNDS FOUND IN IDENTIFICATION SCAN
OF KIDC BOX SAMPLES
Volatile Organic Compounds
1 ,t-Dibromo-2-Chloro-2-Fluoro
-Cyclopropane
Carbon Monoxide
Ethyl Benzene
m/p Xylene
2,4-Dinitrotoluene
2-{2-(EthenyIoxy)Ethonxy)-Ethanol
2,4-lmidazolidinedione
n-Methyl-1 -Octanamine
Benzene
1,3-Dioxolane-2-Methanol
1,1 -Oxybis(2-Ethoxy)-Ethane
Thieno(3,2-C)Pyridine
Semi-Volatile Organic Compounds
(Polynuclear Aromatic Hydrocarbons
and Other Compounds)
Benothiopene
Dibenzofuran
Dimethylnaphthaiene
Dimethylphenol
1H-lndene
Methylnaphthalene
Methyiphenol
Phenol
Styrene
Thiopene
Unknown Aliphatic Hydrocarbon
Unknown Aromatic Hydrocarbon
Unknown Hydrocarbons
Semi-Volatile Organic Compounds
(Phenols. Cresols and Other Compounds^
Benzonitrile
Benzothiopene
Dibenzothiopene
Dimethylnaphthaiene
Ethylphenol
1 H-lndenc
Isoquinoline
Methyldibenzofuran
Methylnaphthalene
C14H10 Substituant Methyl
C3 Substituant Phenol
Trimethylphenol
Unknown Aliphatic Hydrocarbon
27
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4.3 Area Monitorino
4.3.1 Samples for Total Nuisance Particulate and Benzene Soluble Oraanics
Area monitoring of the ambient air quality in the area of the coke oven bench of battery Nos.
11 & 12 was performed. Samples were obtained in accordance with personnel hygiene methods.
The constituents sampled for were total nuisance particulate and the benzene soluble fraction of
total particulate matter (BSFTPM). This constituent is also sometimes referred to as benzene
soluble organics (BSO). These samples were obtained over an eight hour period in the area of
the conventional coke oven door machine. This area was chosen because of its close proximity
to the pushing operation. Each sample was converted to a time weighted average concentration
(TWA).
Sampling of the total nuisance particulate and BSO in the area of the KIDC carrier was
performed in a similar manner to samples which were obtained for the background analysis.
Some modifications to the general procedure needed to be made, however, to avoid biasing
results due to significant non-production periods. For this reason, sampling was performed only
during production periods and not over a full eight hour period.
The results of these area monitoring studies are shown in Appendix D. It is emphasized that
data from the background area monitoring tests and the KIDC area monitoring tests are not
directly comparable because of the inherent differences in the sampling locations and methods.
Laboratory analyses were performed by American Medical Laboratories, inc. Documentation on
their quality assurance program is included in Appendix L.
4.3.2 GC/MS Identification Scan
On October 9,1992, three samples of gases in the area of the conventional coke oven door
machine were obtained for an organics scan by GC/MS. Samples were adsorbed using a
Cartootrap 300 tube over periods ol 5, 10, and 15 minutes. The sampling rate was set at 175
ml/minute using the same personnel hygiene pumps used for the other area monitoring samples.
The flow rate was calibrated just prior to sampling and the samples were obtained side by side
with the same starting time for all three samples. The GC/MS is calibrated daily using the GC/MS
autotune function and a perflourotributylamine standard. Table 4-7 indicates the compounds
identified in the scans and the probability of a match. A report of analysis for this testing from
American Medical Laboratories, Inc. is provided in Appendix D.
28
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TABLE 4-7
GC/MS IDENTIFIED COMPOUNDS FROM AREA SAMPLES
COLLECTED FROM CONVENTIONAL COKE OVEN DOOR MACHINE
Compound Probability of Match
5 Minute Sample
Hexane 91%
Benzene 94%
2,2,3,3-TetramethyI Butane 74%
Toluene 83%
10 Minute Sample
Benzene 95%
Toluene 90%
Xylene 95%
Ethyl Benzene 76%
15 Minute Sample
Methylene Chloride 90%
Hexane 78%
Benzene 94%
4.4 Quenching Emissions
One of lhe environmental benefits of the KIDC system is the elimination of quench tower
emissions. This testing program attempted to estimate the magnitude of the current quenching
emissions from the operation of No. 11 & 12 batteries at Sparrows Point. A sampling program
was undertaken to determine a number of the constituents in the quench water which might be
evolved in the quenching process.
4.4.1 Particulate Emissions
In general, it has been shown that one of the most reliable indicators of total particulate
emissions is the amount of total dissolved solids (TDS) In the quench water. With the assistance
of EPA, a consultant {J. Jeffery) from Alliance Corp. was hired to evaluate the specific design of
the quench tower utilized for the 11 & 12 battery quenching operation and to assess the potential
emissions from them. This report is provided in Appendix E.
29
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Based on previous testing at other steel mills which appear to have similar physical design
characteristics as Sparrows Point's 11 & 12 battery quenching operation, an equation was
developed by Alliance Corp. to provide a correlation between TDS and pounds of particulate
emissions per ton of coal charged. This equation is presented below:
E = 1.31 + 0.000144Y
where:
E = Particulate emissions in lbs. per ton of coal charged
Y =. TDS (mg/l)
The Sparrows Point quench tower is a cylindrical brick tower approximately 100 feet tall
with a diameter of 16.5 feet. Approximately, 8450 gallons of water are sprayed on 10.4 tons of
coke over a 47 second period. Baffles for the control of quenching emissions are installed at the
discharge of the tower. These baffles are constructed of reinforced fiberglass and are spaced
between 4 to 6 inches at an angle of 45 degrees. As reported by J. Jeffery of Alliance Corp., this
design is estimated to be 50 to 60% efficient in the removal of particulate emissions.
21 samples of quench and make-up waters were collected from March through
November 1991. These analyses are presented in Appendix E. The high TDS levels indicated
on March 19 and November 26 are believed to be the result of a cross connection of the quench
water make-up line with an emergency salt water line which may have resulted in the leaking of
salt water into the make-up water system. The make-up water is supplied by the plant industrial
water system which originates from the treated effluent from Baltimore City's Back River municipal
waste water treatment plant. This water is pumped to the Sparrows Point plant where it is
chlorinated and distributed throughout the plant for use as cooling and process water.
Original sampling occurred at two points. The make-up water from a line just upstream of
where the make-up water addition occurs. The initial quench water samples were obtained from
the return waters alter the commence of the quenching cycle as it returns to the quench water
reservoir where suspended solids are removed.
At the request of J. Jeffery, the water sampling location was changed on August 29 to the
water feed line just before the spray nozzles. This sampling location is believed to be the more
representative of the water which actually hits the coke and should therefore provide a better
estimate of quench tower emissions when used with the equation given above. TDS analysis
were performed in accordance with EPA Method 160.1 except that on August 29 the procedure
was modified at the request of J. Jeffery to be run at 103-105 F vs. 180 C as called for in the
procedure. This change was made because prior testing work on which the equation used to
estimate emissions was based used this lower temperature. The average TDS level to be used
in the above equation is therefore 988 mg/l based on the average of seven (7) samples obtained
from August 29 to October 31,1991. The sample on November 26 is excluded from this average
because of apparent salt water contamination of the system on this date which represents an
abnormal operating condition. This yields an emission factor of 1.45 lbs per ton of coal charged.
This (actor is higher than that reported in AP-42 tor clean water quenching with baffle controls of
0.54 lbs. per ton of coal charged. The factor developed specifically for the Sparrows Point
quench tower should, however, more closely represent the actual emissions which could be offset
from the use of the KIDC system. This factor would be specific to this installation and would have
to be re-evaluated to be applied to other installations.
30
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4.4.2 Quench Water TCLP Analysis
Three separate Toxicity Characteristic Leaching Procedure (TCLP) tests were performed
on samples obtained of both the quench waters and the makeup waters. A report of the results
of these tests performed by Bethlehem Steel's Homer Research Laboratory is presented in
Appendix E. These results indicate that this water does not demonstrate the toxicity
characteristics of a hazardous waste as defined by EPA. In fact, the only constituents noted
above the detection level were chloroform and 0, M&P Cresols. Chloroform is a contaminant
found in many treated waters and is a disinfection by-product of the normal water supply
disinfection chlorlnation process. This contaminant is one in the class of compounds known as
trihalomethanes (THM).
31
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5.0 COKE QUALITY & YIELD
A major objective of the KIDC test program was to determine the quality arid yield of the
coke produced by the KIDC system and to compare these results to the coke produced by the
conventional wet quenched process during the same time period.
5.1 Coal Mix
The types and mix of individual coals used for the cokemaking process are the most
important criteria in the production of a high quality, consistent product. Bethlehem designs an
overall coal blend to have a consistent content of sulfur, volatile matter, ash, and size. Individual
coals are varied by type and percent of blend to attain a coal mix that meets this criteria for
proper oven operation and coke quality.
Individual coals used and the blend percentages have been evaluated to properly compare
coke quality between conventionally quenched coke and that produced by the KIDC system.
Baseline comparison data for the conventionally quenched coke began in January 1991.
During 1991, the individual coals comprising the Sparrows Point blend was in two distinct
periods; January - March was a consistent blend, April was a transition month and May - October
was another consistent period. The coal mix percentage was altered slightly in November 1991
as a result of the announced facility shutdown. The monthly blend mix percentages are shown
in Appendix N.
Tables and Graphs presented in Appendix N demonstrate the blended coal mix chemistry
using monthly averages of daily samples taken from conveyor belt #17 located immediately prior
to oven charging.
Despite the two coal mix changes made in 1991, the coal blend chemistry remained
consistent throughout the period. Coal mix bulk density and -1/8" coal size, major contributors
to final coke quality, were especially well controlled throughout 1991.
Coal quality is judged consistent for the comparative analysis of KIDC and conventionally
quenched coke. Furthermore, since coke sample comparisons were made only for conventional
and KIDC coke produced on the same day, any slight blend irregularities occurring on a day to
day basis would be negated.
5.2 Coke Quality
Table 5-1 shows a summary comparison of the physical qualities of the KIDC coke samples
taken during the test and the conventional coke (K-6) produced on both 11 & 12 batteries.
32
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TABLE 5-1
COMPARISON OF KIDC COKE WITH CONVENTIONALLY QUENCHED COKE
KIDC COKE
MEAN
St. Dev.
N
CONV. COKE
MEAN
St. Dev.
N
KIDC COKE
DIFFERENCE
T-test ANALYSIS
T Value
CONFIDENCE
% > 4" % > 2" % < Vz" Moisture Stability Hardness BethReacl CRI
Shatter
Test
CSR Coeff.
21.5
12.2
36
34.6
7.0
43
88.5
10.4
87
93.2
5.3
43
1.5
1.6
87
0.8
05
43
-13.10% -4.70% 0.07%
7.7
99%
3.4
99%
3.7
99%
1.4
M
86
2.5
1.8
43
-1.10"/
3.5
99%
62.8
1.4
85
60.4
0.9
43
2.4
12
99%
69.1
1.3
85
69.2
1.0
43
-C.1
13.7
1.9
86
12.9
1.3
42
0.8
25.7
2.0
92
60.9
3.5
92
26.6* 59.6*
2.2 4.1
0.5 2.9
NO DIFF. 99%
35
-0.9
2.14
95%
53
1.3
1.9
90%
2.7
0.5
73
2.2
0.2
39
0.5
8.3
99%
' Data from September, October, November - Blast Furnace Data.
33
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In order to provide a valid comparative analysis, KIDC coke produced on specific days is
compared only to conventional coke produced on the same specific day. All of the data for each
population is compared using the Student's T-test analysis for the "difference between means"
method. This value determines if the mean and standard deviation values of the two populations
are statistically different at a given confidence level.
By using only the sample data for coke produced on the same day for the two groups it Is
possible to minimize other operational factors such as coal mix, coking and pushing schedules
that could also affect coke quality.
The Student T values shown in Table 5-1 demonstrates that the difference in mean values
for each physical characteristic of the two populations are statistically significant at the indicated
confidence level.
The results of the comparative study are as follows:
1. KIDC coke mean values for size are smaller for all values (% > 4", % > 2", and
% < 1/2") than conventional coke at a 99% confidence level.
2. KIDC coke contains 1.4% moisture compared to 2.5% moisture for the conventionally
quenched coke produced at Battery Nos. 11 & 12. This is a 1.1% reduction in moisture
(about a 50% reduction in moisture). It should be noted that the 2.5% moisture content
of the conventionally quenched coke at Sparrows Point is lower than general industry
averages which typically contain 3 to 8% moisture. Thus, KIDC coke would contain
substantially less moisture than typical wet quenched coke.
3. The stability of the KIDC processed coke averaged 62.8 compared lo 60.4 for the
conventionally processed coke. This is an increase of 2.5 points or 4%.
4. There is no statistical difference in the hardness of the coke between the two
populations. KIDC coke averaged 69.1 and conventional coke averaged 69.2.
5. KIDC coke, in the Bethlehem reactivity test, shows significantly higher values than
conventional coke at a 99% confidence level.
6. Coke reactivity index (CRI) and Coke strength after reaction (CSR) are statistically
different for the populations but only at 95% and 90% confidence levels respectively.
In these tests, the lower the value of CRI, the better. For CSR, the higher the value, the
better. The KIDC coke shows a lower value for CRI and a higher value for CSR than
the conventional coke.
7. KIDC coke is more resistant than conventional coke to degradation due to material
handling as measured by the Drop-Shatter test.
The physical differences observed in the two coke populations does warrant some comment
based on a specific difference in the coke handling systems of the KIDC coke and the
conventional coke. During the design stage of the KIDC system, a coke receiver station was built
to accommodate the discharge of coke from the cooting boxes when high production periods were
reached. The coke was to discharge into the receiver, falling onto a large reservoir of previously
pushed coke. During the trial, high production periods were not realized thus.causing the KIDC
discharged coke to free fall approximately 30 feet without a cushion, into wear tile lined receiver.
The conventional coke, in contrast, was not dropped any appreciable distance when it was loaded
onto the wharf.
34
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Another consideration is the inherent difference in the KIDC system which results in the
collection of the coke breeze (i.e. -1/2"). On a well operated battery these breeze losses can
range from 4 to 10%. Some of the areas of breeze losses with the conventional system may
have been reduced by the KIDC system include:
Losses on the cokeside bench upon door removal and pushing.
Burn-up losses during pushing and transport.
Particulate releases during quenching.
Losses due to water wash to the quench sump.
• Losses during transfer to the wharf.
Losses due to shattering of incandescent coke during water quench.
The considerable fall of the KIDC coke could explain the smaller size fraction observed in
the samples. Previous work performed by the Bethlehem research lab showed that every drop
coke receives, there is a distinct reduction of coke size and a resultant increase in stability. As
mentioned, this mechanical degradation could account for a portion of the increase in stability and
better results in the shatter test exhibited by the KIDC coke samples.
In addition to the summary results in Table 5-1, all of the individual data used for the analysis
are presented in Appendix G.
5.2.1 Quality Assurance of Coke Data
In addition to the routine samples of the KIDC coke, samples were taken by Bethlehem
research personnel and submitted to Consol Coal Company in Library, PA for testing. The
purpose of this testing was to assure that the physical and chemical test results obtained at the
Sparrows Point Laboratory were repeatable and accurate when compared to another facility. The
results of this testing are presented in Appendix G along with the other coke data. This data
shows comparable results for all coke properties tested with the results obtained at the Sparrows
Point Laboratory and at the Hampton Roads Testing Labs where CRI and CSR testing was
performed.
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6.0 IMPACT OF KIDC COKE ON BLAST FURNACE OPERATIONS
Bethlehem has developed a computer model which has been used successfully to evaluate
the impact of various burden changes on blast furnace operations. This model is referred to as
the Primary Facilities (BAlWAX) model. It is used to predict the technical and economic benefits
of using the KIDC coke in the blast furnace. A description of the BALWAX model is provided in
Appendix H. The inputs to the BALWAX model include the results of the KIDC coke quality
analysis presented in section 5.
Some of the key baseline inputs and assumptions used in the BALWAX analysis in order to
evaluate the impact on Sparrows Point's L' Blast Furnace are as follows:
'L' Blast Furnace Production 9000 NTHM/day
Coke Rate 860 LB/NTHM
Oxygen Enrichment 1 %
Natural Gas 70 LBS/NTHM
A report of the results of this BALWAX model study is presented in Appendix H. A summary
of the effects of the quality changes noted in the report are as follows:
Moisture Effect
• The decrease in the average coke moisture from 2.5% to 1.4% or an approximate one
percentage point decrease in moisture could result in a reduction of the coke rate of
7 lbs per net ton of hot metal (NTHM). This would permit an increase in the hot metal
production of 73 NTHM/day if demand for the hot metal Increased. It should be noted,
however, that for the base case used in the model these benefits might not be realized
due to a furnace top temperature high enough to drive off the additional moisture in the
conventionally quenched coke. Higher coke moisture levels typically found in the
industry of 3 to 8%, however, could result in a realization of these benefits.
Stability Effect
• The increase in coke stability from 60.4 to 62.8 or an increase of 2.4 points could be
partially due to the excessive drop received by the KIDC coke which has a stabilizing
effect A one point increase in stability is projected to give a decrease in the coke rate
of 5 Ibs/NTHM and an increase in the wind volume of 1%. The increase in wind volume
is the result of an increase in the porosity of the burden in the furnace which would allow
more wind to pass through. The combined effect of the decreased coke rate and the
Increase in wind volume could give a production gain of 146 NTHM/day if demand for
production warranted.
Size Effect
• The decrease in coke size would tend to decrease the production capabilities of the
furnace, but since the size difference experienced in this testing program are believed
to have occurred from the specific coke handling characteristics of the system rather
than from the process itself, these differences are not included as an effect on blast
furnace performance.
36
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Reactivity Effect
• The conflicting results on the two reactivity tests which show an increase in the
Bethlehem reactivity and a decrease in the Coke Reactivity Index (CRI) suggest that
these changes may not be significant. Therefore, no change In this parameter is
assumed in the model.
The overall effect of a one percentage point decrease in coke moisture and a one point
increase in stability would be to reduce annual coke consumption from 1,414,000 of net tons per
year to 1,394,000 net tons per year. This is a decrease in total coke consumption of 20,000 net
tons per year for a constant production rate of 9,000 tons of hot metal per day.
37
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7.0 KIDC OPERATING COSTS
Tha KIDC system did not operate in a sustained production mode. Thus, no reliable
production cost data are available. For a fully operationally system, Bethlehem anticipated cost
saving in the areas of:
• Labor;
• Improved coke quality with subsequent improvements in blast furnace performance; and
• Increased coke yield.
Anticipated savings would be site specific for each installation.
The Kress Corp. did compile a detailed set of costs, for the period October 1, 1991 to
November 26, 1992, for carrier and box maintenance costs. These data are presented in
Appendix I.
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8.0 KIDC BOXES
The original estimate of KIDC operating costs included an assumption for the economic life
of the boxes. This estimate assumed the life of each box to be about one year. Based on a
production level for both Nos. 11 & 12 batteries of 132 pushes per day with 20 boxes, each box
would have had to last approximately 2300 pushes. An attempt was made to verify this estimate
by collecting box thickness data both before and after the demonstration. However, because of
the small number of pushes on each box and the unreliability of the data obtained, it Is not
possible to make reliable estimates of erosion/corrosion effects on the box metal thickness.
8.1 Erosion/Corrosion of Steel Plates
KIDC box wear data was obtained with the use of an ultrasonic thickness gauge. Surface
preparation consisted of scraping with a putty knife and/or a wire brush. A glycerin gel "couplant"
supplied with the gauge was used to obtain reliable readings. In some cases, the surface pitting
on the exterior required extensive surface preparation with the scrapers to get a reading. In order
to minimize any bias to the data, no grinder or emery cloth was used to prepare the surface.
Initial readings were obtained on box Nos. 8 & 9 before any pushes had been accepted by
these boxes. The intent of obtaining this information was to get initial readings to compare with
readings after the boxes had been in service for an extended period of time. Boxes 8 and 9,
however, did not receive enough pushes to reliably determine the extent of erosion and corrosion
that could be expected on the boxes over an extended period of time. A summary Table in
Appendix J presents the number of pushes accepted by each box along with erosion and
corrosion that was measured.
Original thickness readings were not obtained on any of the other boxes. Readings obtained
at the conclusion of the demonstration in the front and middle sections of the box were compared
with readings obtained at the back end of the box. Erosion and corrosion should have been
minimal at the back of the box since the coke never penetrates into this region. The reliability
of this data is limited, however, because of the broad range of the original mill tolerances which
were reported to be 0.240 to 0.290 inches. In addition, paint thicknesses measured were in the
range of 0.006 to 0.008 inches. This paint generally pealed off in the front and middle sections
but remained intact at the far end of the box. These factors all contribute to the poor reliability
of the data obtained.
All of the thickness readings taken are presented in Appendix J. A summary of the
erosion/corrosion on each box was developed by taking the differences between the average
thickness reading at the end of each box and the thickness at in the front and middle of the
boxes. These readings show no correlation between the number of pushes on each box and the
erosion/corrosion measured. This is illustrated graphically in Appendix J which shows the erosion
and corrosion on each box vs. the number of pushes. No conclusion with respect to box life can
therefore be made from this data.
39
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8.2 Maintenance Observations
Visual observation of the boxes following the demonstration showed the external pitting to
be the worst on box #3 which logged the highest number of pushes, ninety (90). Other boxes
also showed pitting but to a lesser degree than box #3.
Operating experience with the boxes revealed that several boxes required exterior bracing
to correct "hourglassing" in the center after a relatively few number of pushes. In addition, many
of the boxes required replacement of the internal gas ductwork. These items along with the
adjustment and replacement of seals at the funnel section would be routine maintenance items
that could be expected. The funnel section is the open portion of the box which is aligned with
the oven. This Is referred to as the "front" of the box and It is the first part of the box that the
coke passes through as it is pushed from the oven. Other items performed during the
demonstration such as changes to the spatula design were non-routine. The spatula is a ram
inside the rear of the box which is activated by an arm outside of the box during the dump cycle
and is used to assist in the removal of coke by pushing against the coke mass. A picture and
diagram of the KIDC carrier and box is provided in a Kress Bulletin in Appendix 1. Additional
items which could not be evaluated due to the shortness of the test period, but might be expected
to impact the box maintenance cost are:
• Maintenance of box circulating fans
• Replacement of box bottom plates
• Periodic grit blasting and painting of box exteriors
A listing of all of the maintenance items performed on the boxes during the demonstration
period which indicates items which would be considered to be routine has been provided by the
Kress Corporation and is presented in Appendix I. Also presented in Appendix I is a listing of all
maintenance performed on each box and the associated cost.
8.3 KIDC Water System Treatment
The KIDC cooling water system was not treated during the demonstration because of the
limited operational time period anticipated. A report by Betz MetChem presented in Appendix J
provides an analysis of the water during the demonstration. This report indicates that the system
was running at 4.3 cycles of concentration which is higher than their recommended level of 3
cycles. The recommendations of Betz MetChem for treatment and the anticipated costs are also
presented in Appendix J. The anticipated annual treatment cost for this system was $28,000.
40
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9.0 KIDC RELIABILITY
The long term reliability of the KIDC system cannot be adequately projected from the short
demonstration testing performed at Sparrows Point. Many of the maintenance items which
needed to be addressed during the testing program were items which when corrected initially
would not be expected to re-occur due to fundamental design corrections. Other maintenance
items which might impact on the reliability of the carrier over the long term could not be evaluated
in such a short time frame. A list of the maintenance items and the associated costs performed
on both the carrier and the boxes during the demonstration testing is presented In Appendix I.
This list also attempts to indicate which items are considered to be regular maintenance items.
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10.0 KIDC CYCLE TIME
The average cycle time for the KIDC system during the two month demonstration was
derived from the push times recorded by the VEO readers. These data indicate an overall
average of 27.75 minutes between pushes for the two month demonstration. On a monthly basis,
the cycle times were 28.58 minutes and 21.36 minutes for October and November respectively.
This compares to an average of 15.15 minutes for the conventional pushing systems over the
same time period. On a monthly basis, the conventional cycle time was 18.06 minutes and 10.20
minutes for October and November respectively. It should be noted that ttiese cycle times reflect
the total time between pushes. This would include delays caused by coke oven operations on
occasion. In addition, these cycle times in some instances are influenced by removal of the coke
oven door by Bethlehem's door machine, and the use of an empty box from the cooling rack
without having to unload. The KIDC carrier never achieved operation in its fully automated mode
and as a result the average cycle time observed was longer than originally anticipated. In
addition, significant increases in the travel speed of the carrier projected by Kress Corporation
for future testing could reduce average cycle times furttier.
For analysis, all cycle times greater than one hour were eliminated from the data set as
these times could include down time due to the scheduling of production or extended
maintenance delays. Table 10.1 presents a summary of the cycle times for the KIDC system and
the conventional pushing systems. These data are also presented graphically in Figure 10.2.
TABLE 10-1
CYCLE TIMES FOR THE KIDC AND CONVENTIONAL PUSHING SYSTEMS
OCTOBER
NOVEMBER
OVERALL
KIDC
AVERAGE
(MINUTES)
28.58
21.36
24.75
STANDARD
DEVIATION
7.34
6.43
7.74
CONVENTIONAL
AVERAGE
(MINUTES)
18.06
10.20
15.15
STANDARD
DEVIATION
11.01
3.43
9.68
42
-------
CO
Figure 10-2
Average Time Between Push Comparison
Kress and Conventional Pushes
Sparrows Point 11 & 12 Battery
08/01/91 - 11/26/91
CD
>
<
co
(D
sz
(/)
D
Q_
C
(D
CD
<:
CD
_Q
CO
CD
13
C
100
90
80 H
70
60
50 H
40
30
20
10
0
Legend
• Kress puahee
= Conventional Pushes
— A A' /'¦
/ \\ / \J ,,v
/ \v »
/
\
1 1 1 1 1 1 1 1 : 1 1 r 1 r — ~ 1 r
1 8 IB 22 29 6 12 19 26 3 10 17 24 31 7 14 21 26
AUGUST SEPTEMBER OCTOBER NOVEMBER
1991
100
-90
80
70
60
50
40
30
20
10
0
a>
>
<
in
CD
CO
D
Q_
<5
0
0
_Q
CO
-------
11.0 COOLING TIMES
A satisfactory cooling time is established by the temperature of the coke when unloaded.
The temperature standard established by Bethlehem to ensure the protection of related
processing equipment was 400 F. The specific process equipment of concern are the conveyor
belts which are used to move the coke from the receiving coke hopper to Ihe blast furnace.
These belts are rubber which when exposed to excessive temperatures will melt resulting In
premature failure. II has also been found that coke if not cooled sufficiently when left in a pile
or in a hopper will reignite.
The temperature of the coke was measured by two ircon temperature sensors which were
mounted after the receiving coke hopper. The sensor noted as FS-1 indicates the temperature
of the coke at the bottom of the K-6A conveyor belt which is the first point that the coke contacts
after being discharged from the coke receiving hopper vibrating feeder. The sensor noted as
FS-2 indicates the temperature of Ihe coke at the tail end of the K-6A belt just before the belt
water sprays. These sensors were calibrated by the manufacturer on October 2, 1991, and a
report of that calibration is included in Appendix K. All available strip chart recordings showing
the temperature vs. time for various pushes are provided in Appendix K. Table 11-1 shows the
cooling times and the estimated peak and average temperatures from each of the charts. A plot
of the overall estimated average temperatures vs. cooling time is shown in Figure 11 -2. The
temperature used for this plot is the average of FS-1 and FS-2 taken from Table 11-1. For
graphical purposes, all average temperatures which were >600 F or <250 F are presented as 600
and 250 F respectively. In addition, all data which indicated overnight cooling was assumed to
have cooled for 20 hours. FS-1 temperature readings are in general higher than the readings
from FS-2 because of the location at which the readings are made. This suggests that rapid
cooling ot the coke is occurring as it is run out onto the conveyor belt.
From this data, it appears that a cooling time of approximately 4.5 hours would be required
to achieve an average temperature of 400 F. A longer time period would be required to achieve
Bethlehem's internally accepted standard of 90% of the coke less than 400 F and a maximum
temperature of 550 F.
The greenness of the coke experienced during the demonstration is not believed to have
adversely affected the KIDC cooling times, but in the absence of comparative test data, no
conclusion can be made as to the impact, if any, this might have had on the cooling operation.
Surface pyrometer temperatures of the coke were taken in addition to the temperatures
obtained from the sensors mounted after the receiving hopper. These temperatures were in
general considerably lower. The reasons for this difference were never fully explained but may
have been partially due to the rapid surface cooling of the individual coke pieces once removed
from the coke pile. These data have not been included in this report due to questions regarding
the quality and representativeness of the data.
11.1 Three-Dimensional Heat Transfer Modeling
Heat transfer modeling was performed to provide an indication of the theoretical cooling
times required to cool the coke mass within the KIDC box. The results of this modeling indicate
that an average temperature of 400°F can be achieved after about six hours of cooling. A
discussion of the methods used in this modeling and the results are provided in Appendix K.
44
-------
TABLE 11-1
KIDC COOLING TIMES AND DISCHARGE TEMPERATURES
FS-1/FS-2
FS-1/FS-2
DATE
PUSH
OVEN#
BOX#
COOLING TIME
MAX. TEMP
AVE. TEMP
10/18
130
1153
5
2:38
>600/> 600 F
>600/>600
10/18
131
1149
8
2:40
>600/ 600
545/ 491
10/18
132
1152
3
2:41
>600/ >600
>600/ 545
10/18
133
1154
5
2:52
>600/ >600
>600/ 600
10/19
137
1148
3
2:47
>600/>600
>600/ 447
10/19
138
1151
8
2:38
>600/ 600
589/ 359
10/19
139
1153
5
2:55
>600/ >600
>600/ 545
10/19
140
1149
3
3:00
>600/ 462
458/ 370
10/19
141
1152
6
2:47
>600/ 526
545/ 392
10/19
142
1154
5
20:12
324/ 303
294/ 261
10/19
143
1135
3
18:28
38&' 579
338/ 370
10/19
144
1171
6
18:29
314/ 324
272/ 272
10/20
145
1151
5
2:55
>600/ 452
578/ 338
10/20
146
1148
3
2:58
579/ 568
491/ 436
10/20
147
1153
6
2:51
>600/ 324
556/ 414
10/20
148
1149
5
2:48
>600/ 579
502/ 458
10/20
149
1152
3
2:46
579/ 590
447/ 502
11/7
228
1148
2
2:53
>600/ 600
473/ 356
11/7
229
1151
5
2:49
600/ 600
483/ 377
11/7
230
1153
3
2:47
600/ 600
462/ 377
11/7
231
1149
6
2:47
>600/ >600
568/ 473
11/7
232
1172
2
2:41
>600/ >600
590/ 558
11/7
233
1152
5
2:32
>600/ >600
547/ 515
11/19
249
1148
3
2:54
>600/ >600
536/ 494
11/19
250
1151
9
2:43
>600' >600
568/ 547
11/19
251
1153
5
2:39
>600/ >600
600/ 483
11/19
252
1149
6
Overnight
<250/ 348
<250/ 250
11/19
253
1172
4
Overnight
425/ 600
324/ 377
11/19
254
1152
8
Overnight
260/ 359
<250/ 250
11/19
255
1135
7
Overnight
523/ 600
314/ 324
11/19
256
1154
1
Overnight
469/ 600
271/ 314
11/19
257
1171
2
Overnight
<250/ 381
<250/ 261
11/20
258
1148
3
4:27
>600/ >600
388/ 420
11/20
259
1151
9
4:25
>600/ >600
399/ 399
11/20
260
1153
5
4:21
578 600
441/ 441
11/20
282
1172
4
Overnight
<250/ <250
<250/ <250
11/21
267
1148
3
5:46
480/ 600
356/ 388
11/21
268
1151
9
4:50
502/ 523
377/ 420
11/21
269
1153
5
4:46
512/ 556
377/ 388
11/22
276
1148
3
3:39
>600/>600
473/ 388
11/22
277
1151
9
3:41
>600/ 600
452/ 409
11/22
278
1153
5
3:34
>600/ 589
494/ 388
11/23
288
1148
7
3:01
>600/>600
579/ 388
11/23
289
1151
3
3:03
>600/ 556
515/ 367
11/23
290
1153
9
2:59
>600/ 545
473/ 388
11/25
306
1148
7
4:11
578/ 567
441/ 409
45
-------
4^
Cb
LL
LU
FIGURE 11-2
KIDC COKE TEMPERATURE VS. COOLING TIME
Sparrows Point 11 Battery
650
C/5
<
250
0
i
4
8
10
12
14
16
18
20 22
COOLING TIME- Hours
-------
12,0 CAPITA!. COSTS
The system was to have been demonstrated first on No. 11 Battery. If successful, the
system would have expanded to include No. 12 Battery. Both internal Bethlehem capital
appropriation procedures and Bethlehem's contract with EPA recognized this two step process.
^•1 Phasq I Concept Costs
The capital cost for the first phase was estimated and approved by Bethlehem's Board of
Directors to be $10 million. The $10 million included a $6,685,840 firm price contract with the Kress
Corporation.
Included In the $6,685,840 was:
1. 1 coke Receiver Station
2. 1 coke Container Cooling Rack
3. Maintenance Building
4. a rail guide system
5. electrical facilities
6. 1 carrier
7. KIDC Engineering
8. 10 coke containers
Additional capital costs included:
Aids to construction $ 200,000
Site Preparation 738,600
Construction Management 258,000
Bethlehem Engineering 1,020,000
Spares 200,000
Other 905.560
$3,314,160
Actual Phase I costs were $11 million. The higher than estimated costs resulted from: design
and construction of the receiver station; reinforcement of coke bench and carrier guide rail due to
increased weight of the carrier; labor premium time to meet obligated schedule dates and
reinforcement of the roadway network. KIDC contract costs were those as negotiated and settled
by the parties. Such costs were based upon the specific physical characteristics/constraints of
Sparrows Point's Eleven Battery.
47
-------
12.2 Phase II Concept Costs
Phase il of this project was never done because of the idling of the coke batteries in
December 1991. Had Phase II been implemented the additional estimated costs were:
Additional Equipment/Engineering $6,000,000
Project Management 13,000
Demonstration 370,000
Testing 69,000
Operating {14 months) 2,608,000
Total $9,060,000
The additional equipment would have been:
• two additional carriers
• ten additional boxes
• one coke container cooling rack
This estimate was based on the original scope of the project prior to the Phase I tests.
These costs would need to be reviewed and updated based on new information and any change
in scope. The shortened test period; however, makes it difficult to assess the need for the
additional equipment which was originally assumed.
48
-------
13.Q SUGGESTIONS FOH FUTURE WORK
The limited scope and time frame of the testing at Sparrows Point prevented determination
of the overall long-term viability ol the KIDC system. Although the performance of the KIDC
system showed promise, many key parameters could not be evaluated with confidence. There
also appears to be the potential for improvement in many areas as the KIDC system evolves.
For these reasons, additional testing is recommended in the following areas:
• Confirm the results of all testing performed to date.
• Test a new coke receiving station design or operate the existing receiving station in a
mode which would not degrade coke quality and re-evaluate the KIDC coke quality vs.
conventionally quenched coke.
• Test improved burner designs and controls to minimize emissions from the box flare
stack. Even though the emissions from KIDC pushes were significantly lower than
conventional pushes, further improvements could be obtained by improvement to this
flare.
• Evaluate new designs to minimize further any leakage from the box to jamb interface.
New jambs which may be within closer tolerances than what was experienced on Battery
No. 11 during the testing may provide an easier application for the sealing and alignment
of the KIDC boxes to the oven.
• Develop long-term operating cost information.
• Obtain more extensive information on box wear characteristics (both inside and outside
the box).
• Additional testing on the amount of cooling time needed to adequately cool the coke.
This would include an evaluation of the effect of "green" coke, gas recirculation, changes
in box design and other factors which might impact cooling times. All of these factors
would need to be taken into consideration in order to optimize the number of boxes and
cooling rack stations for engineering and cost evaluations.
• Determination of the reliability of the total system over an extended time frame and over
wide ranging seasonal conditions.
• Visible emission observations should attempt to evaluate average opacity levels rather
than maximum opacity to give a better approximation of true overall emissions.
-------
REFERENCES
1. Vajda, Stephen, "Evaluation of the KIDC System for Coke Oven Pushing and
Quench Tower Emission Control Issued in Compliance with DOE Grant DE-FG01 -
8SCE15227," S & E Consultants, Inc., Pittsburgh, PA.
2. Tucker, J., Everett, G., and Hall, G., "Coke Breakage During Oven Discharge," 1991
Ironmaking Conference Proceedings, p. 211-223.
3. Chmielewski, D.F., and Serdy, J. R., "The Determination of Variability within a
Commercial Coke Oven Via Repeated Excavation of a Dry Quenched Charge,"
AIME, Ironmaking Proceedings, Volume 46 (1989).
4. Carpenter, G. C., "KIDC - A Major Breakthrough in Emission Control", Kress
Corporation, October 25,1991.
50
-------
Appendix A
Visible Emission Observation Data & Summary Tables
Table of Contents
Sect ion Page
1 KIDC Box Flare Stack and Pushing Observations vs. A-2
Conventional Pushing Emissions - Overall & Monthly.
2 Analysis of Conventional Controls - Chemico Car vs. A-7
Shenango Car.
3 KIDC Box Flare Stack and Pushing Observations e, A-ll
Conventional Pushing Emissions - Database.
4 Pushing Emissions T-test Comparison of the Conventional A-3B
Control Systems vs. the KIDC System.
A-l
-------
Section 1
KIDC Box Flare Stack and Pushing Observations vs. Conventional
Pushing Emissions - Overall & Monthly
A-2
-------
KIDC BOX FLARE STACK AND PUSHING STATISTICS
OVERALL STATISTICS
OCTOBER - NOVEMBER, 1991
AVERAGE STANDARD MAXIMUM MINIMUM NUMBER
VALUE DEVIATION VALUE VALUE OF OBS
IGNITION DELAY, SECONDS
21.3
23.9
240
0
196
PUSH EMISSION TIME, SECONDS
72.1
39.2
443
10
232
TRAVEL EMISSION TIME, SECONDS
120.6
83.0
492
0
242
MAXIMUM OPACITY BEFORE IGN., %
20.4
10.6
55
0
245
MAXIMUM OPACITY AFTER IGN., %
CM
CM
r—1
6.9
40
5
217
MAXIMUM OPACITY AT BOX/JAMB CONN.,
9.1
5.9
40
0
228
KIDC EOX FLARE STACK AND PUSHING STATISTICS
MONTHLY STATISTICS
AVERAGE STANDARD MAXIMUM MINIMUM NUMBER
VALUE DEVIATION VALUE VALUE OF OBS
OCT 91
IGNITION DELAY,
SECONDS
26.5
26.9
150
2
119
PUSH EMISSION T:
:me, SECONDS
77.3
43.9
443
1C
125
TRAVEL EMISSION
TIME, SECONDS
114.6
91.4
492
0
137
MAXIMUM OPACITY
BEFORE IGN., %
22.3
11.5
55
0
138
MAXIMUM OPACITY
AFTER IGN., %
12.7
7.2
40
-
120
MAXIMUM OPACITY
AT BOX/JAMB CONN.,
6.5
5.2
25
125
NOV91
IGNITION DELAY,
SECONDS
13.2
30.2
240
c
77
PUSH EMISSION T:
:me, SECONDS
65.4
31.6
256
12
107
TRAVEL EMISSION
TIME, SECONDS
128.4
70.3
360
0
105
MAXIMUM OPACITY
BEFORE IGN., %
17.9
8.9
40
5
107
MAXIMUM OPACITY
AFTER IGN., %
11.6
6.5
30
5
97
MAXIMUM OPACITY
AT BOX/JAMB CONN.,
9.7
6.7
40
103
A-3
-------
CONVENTIONAL CONTROLS
PUSHING EMISSIONS CONTROL STATISTICS
OVERALL STATISTICS
MARCH - NOVEMBER, 1991
AVERAGE STANDARD MAXIMUM MINIMUM NUMBER
VALUE DEVIATION VALUE VALUE OF OBS
PUSHING EMISSION TIME, SECONDS
71.6
52.1
737
0
628
TRAVEL EMISSION TIME, SECONDS
46.9
20.3
121
0
626
TOTAL EMISSION TIME, SECONDS
118.1
57.6
791
0
627
OPACITY DURING PUSH, MAX. %
69.0
28.7
100
0
629
OPACITY DURING TRAVEL, MAX. %
32.1
24.1
100
0
624
A-4
-------
CONVENTIONAL CONTROLS
PUSHING EMISSIONS CONTROL STATISTICS
MONTHLY STATISTICS
AVERAGE STANDARD MAXIMUM MINIMUM NUMBER
VALUE DEVIATION VALUE VALUE OF OBS
MAR91
PUSHING EMISSION TIME, SECONDS
61.3
63.5
440
42
38
TRAVEL EMISSION TIME, SECONDS
58.9
23.1
121
17
38
TOTAL EMISSION TIME, SECONDS
139.9
64.5
486
73
38
OPACITY DURING PUSH, MAX. %
62.2
32.4
100
0
38
OPACITY DURING TRAVEL, MAX. %
23.9
22.4
85
0
38
APR91
PUSHING EMISSION TIME, SECONDS
53.9
20.4
121
0
79
TRAVEL EMISSION TIME, SECONDS
38.6
25.8
112
0
79
TOTAL EMISSION TIME, SECONDS
92.6
40.2
174
0
79
OPACITY DURING PUSH, MAX. %
58.9
31.6
100
0
79
OPACITY DURING TRAVEL, MAX. %
18.9
16.8
60
0
79
MAY91
PUSHING EMISSION TIME, SECONDS
58.3
45.8
452
19
90
TRAVEL EMISSION TIME, SECONDS
43.1
17.3
82
0
90
TOTAL EMISSION TIME, SECONDS
111.4
51.6
515
41
90
OPACITY DURING PUSH, MAX. %
70.7
29.3
100
5
90
OPACITY DURING TRAVEL, MAX. %
31.1
20.3
100
C
89
JUN91
PUSHING EMISSION TIME, SECONDS
81.6
83.8
572
41
70
TRAVEL EMISSION TIME, SECONDS
44.4
15.4
SO
21
70
TOTAL EMISSION TIME, SECONDS
125.8
82.7
596
69
70
OPACITY DURING PUSH, MAX. %
65.2
27.5
ICO
10
70
OPACITY DURING TRAVEL, MAX. %
26.1
22.0
100
0
70
JUL91
PUSHING EMISSION TIME, SECONDS
65.7
22.8
209
0
108
TRAVEL EMISSION TIME, SECONDS
49.8
22.2
107
0
108
TOTAL EMISSION TIME, SECONDS
115.4
34.6
249
0
108
OPACITY DURING PUSH, MAX. %
68.6
27.4
100
0
109
OPACITY DURING TRAVEL, MAX. %
35.1
27.4
100
0
107
AUG91
PUSHING EMISSION TIME, SECONDS
70.8
27.9
226
39
90
TRAVEL EMISSION TIME, SECONDS
52.2
21.7
98
0
78
TOTAL EMISSION TIME, SECONDS
122.2
39.0
307
40
79
OPACITY DURING PUSH, MAX. %
72.5
27.5
100
10
30
OPACITY DURING TRAVEL, MAX. %
37.0
25.9
100
0
78
SEP91
PUSHING EMISSION TIME, SECONDS
71.6
12.4
116
52
76
TRAVEL EMISSION TIME, SECONDS
50.3
15.4
06
n
76
TOTAL EMISSION TIME, SECONDS
122.0
22.3
231
52
76
OPACITY DURING PUSH, MAX. %
"6.4
25.8
100
10
76
OPACITY DURING TRAVEL, MAX. %
47.8
26.1
100
0
76
A-5
-------
CONVENTIONAL CONTROLS
PUSHING EMISSIONS CONTROL STATISTICS
MONTHLY STATISTICS
OCT91
PUSHING EMISSION TIME, SECONDS
TRAVEL EMISSION TIME, SECONDS
TOTAL EMISSION TIME, SECONDS
OPACITY DURING PUSH, MAX. %
OPACITY DURING TRAVEL, MAX. %
NOV 91
PUSHING EMISSION TIME, SECONDS
TRAVEL EMISSION TIME, SECONDS
TOTAL EMISSION TIME, SECONDS
OPACITY DURING PUSH, MAX. %
OPACITY DURING TRAVEL, MAX. %
AVERAGE STANDARD MAXIMUM MINIMUM NUMBER
VALUE DEVIATION VALUE VALUE OF OBS
31.4
92.2
737
31
55
44.9
17.8
101
10
55
125.8
96.8
791
41
55
71.8
28.3
100
10
55
31.7
21.5
100
5
55
96.7
79.5
420
36
32
42.3
9.7
67
20
32
139.0
79.9
463
77
32
76.1
25.5
100
15
32
31.4
19.3
100
5
32
A-6
-------
Section 2
Analysis of Conventional Controls
Chemico Car vs. Shenango Car
-------
PUSHING EMISSIONS CONTROL STATISTICS
OVERALL STATISTICS 3Y EMISSION CONTROL
MARCH - NOVEMBER, 1991
CHEMICO CAR
AVERAGE STANDARD MAXIMUM MINIMUM NUMBER
VALUE DEVIATION VALUE VALUE CF OBS
PUSHING EMISSION TIME, SECONDS
61.9
19.8
209
0
153
TRAVEL EMISSION TIME, SECONDS
47.5
21.9
121
0
152
TOTAL EMISSION TIME, SECONDS
108.9
33.2
255
0
153
OPACITY DURING PUSH, MAX. %
67.6
28.6
100
0
153
OPACITY DURING TRAVEL, MAX. %
29.0
20.9
90
0
152
SHENANGO CAR
AVERAGE STANDARD MAXIMUM MINIMUM NUMBER
VALUE DEVIATION VALUE VALUE CF OBS
PUSHING EMISSION TIME, SECONDS
74.7
58.5
737
10
475
TRAVEL EMISSION TIME, SECONDS
46.7
19.8
113
c
474
TOTAL EMISSION TIME, SECONDS
121.4
63.2
791
10
474
OPACITY DURING PUSH, MAX. %
69.5
28.8
100
0
476
OPACITY DURING TRAVEL, MAX. %
33.1
25.3
IOC
G
472
A-8
-------
PUSHER SIDE OVEN EMISSIONS OBSERVATIONS STATISTICS
CHEMICO PUSHES
OVERALL STATISTICS
MARCH - NOVEMBER, X991
AVERAGE
VALUE
STANDARD
DEVIATION
MAXIMUM MINIMUM
VALUE VALUE
NUMBER OF OBSERVATIONS » 58
CUMULATIVE EMISSION TIME, SECONDS 57.7 26.1
MAXIMUM OPACITY, % 45.1 33.4
9S
100
5HENANG0 PUSHES
OVERALL STATISTICS
MARCH - NOVEMBER, 1991
AVERAGE
VALUE
STANDARD
DEVIATION
MAXIMUM MINIMUM
VALUE VALUE
NUMBER OF OBSERVATIONS =225
CUMULATIVE EMISSION TIME, SECONDS 57.3 30 .i
MAXIMUM OPACITY, % 53.0 32.<
165
100
A-9
-------
COKE CVSN TOPSIDE EMISSIONS OBSERVATIONS STATISTICS
CREMICO PUSHES
OVERALL STATISTICS
MINIMUM
VALUE
0
0
MINIMUM
VALUE
0
0
A-10
AVERAGE
VALUE
STANDARD
DEVIATION
MAXIMUM
VALUE
NUMBER OF OBSERVATIONS3 76
CUMULATIVE EMISSION TIME, SECONDS 54.2 36.3
MAXIMUM OPACITY, % 43.6 31.1
210
100
SHENANGO PUSHES
OVERALL STATISTICS
AVERAGE
VALUE
STANDARD
DEVIATION
MAXIMUM
VALUE
NUMBER OF OBSERVATIONS= 236
CUMULATIVE EMISSION TIME, SECONDS 54.0 56.0
MAXIMUM OPACITY, % 48.3 34.2
585
100
-------
Section 3
KIDC Box b'lare Stack and Pushing Observations & Conventional
Pushing Emissions - Database
-------
KRFSS BOX FLARr 6 PUSHING 06SERVA?ION5 10:40 Tuesday, March 31. 1992 I
KRFSS OF MONST RAt I ON I'ROJECl - BETHLEHEM STELL CORPORATION
SPARROWS POINT. MARYLAND
T 1 ML
WI NO
TIMl
- 1 >
NDR T H
1 151
G
1212
12 13
IS
10/08/91
1 1
GW
CLEAR
NW
6-12
NORTH
1 1 h3
3
1239
1240
1<1
•0/08/91
GW
CI EAR
NW
G 12
NOR111
14 4a
2
1433
1433
V-Ci
•O/OA/91
1 1
GW
CLf AR
NW
C 12
NORTH
1 1 b2
b
1503
1504
2 1
10/08/91
1 1
GW
CLEAR
NW
6-12
NOR I'M
1 154
3
1542
1542
DBS
ICNIT TON
DElAf,
SFCONUS
FMFS4»1 ON
T I MP
DURING
PUSH.
SFCONOS
EMISSION
T IMF
DURING
TRAVEL.
SECONDS
MAXIMUM
siack
opacif y
CCFORE
ICNITION.
MAXIMUM
ST ACK
OPACITY
AFTCR
IGNITION.
MAX 1 MUM
DPAC 1T V
AT BOX/JAMB
INTERFACE.
COHMfcNlS
1
2
3
4
5
G
7
8
9
10
1 1
i:>
t j
14
15
1C
17
18
19
20
2 1
32
84
49
43
120
150
63
bfc
IB
08
34
24
71
46
04
172
123
97
131
hV
315
350
87
168
1 12
1«3
134
326
192
2SG
103
4 b
t :>9
101
103
135
96
4 9
183
157
58
20
35
5
20
5
30
10
20
20
2b
3b
3b
45
40
O
2 b
40
25
30
25
20
25
40
1b
1b
1b
15
20
20
10
NU I UN! IiUN
10
5
10
15
20
NiO IGNITION
-------
KRFSS ROX FtARF ft PUSHING ORSFRVATTONS
KPFSS DEMONSTRATION PROJECT - BETHLEHEM STEFl CORPORA 1 ION
SPARROWS POINT. MARYI AND
10 40 Tucsciav. March 31. 1992 2
I I ME
WIND
1 1Mb
Oh
COKE
OBSERVERS
WIND
SPEED.
OBSERVER
OVEN
KRESS
OF
n ARE
OBS
DAT t
BAJTERY
INITIALS
WEATHER
DIRECfION
MPH
LOCATION
PUSHED
BOX NO
PUSH
IGNITION
22
10/09/T1
1 1
o.w
CI f AW
SE
b 10
NnRTH
1 148
2
1 140
1147
23
10/09/91
1 1
GW
CLEAR
SE
5- 10
NORTH
1 1b1
6
1209
24
10/09/9 1
1 1
GW
LLC AR
SE
b 10
NOR in
1 15 J
3
1 2'JB
1239
2 b
1O/09/91
1 1
GW
CLEAR
SE
b- <0
NOR I H
1 119
b
H 14
U 15
26
10/09/91
1 1
GW
CLEAR
SE
f,- 10
NUR1H
1 152
2
1500
1SO?
27
10/C9/91
1 <
GW
CLf AR
SE
5- IO
NORTH
1 154
3
1529
1530
58
<0/09/91
1 1
CW
CI FAR
SF
5- 10
NORTH
1 101
5
1743
1745
29
10/09/91
! 1
(;w
CI FAR
se
b- ',0
NORTH
1 Ub
2
1802
1603
no
1O/09/91
1 1
CW
CI FAR
SF
5 - IO
NT1PTH
117 1
3
1622
1622
31
'0/10/91
1 1
GW
Ct EAR
sw
4 ft
NORTH
1 148
b
1 157
1 157
32
W/ 10/91
1 1
GW
CLEAR
sw
4 0
NOK1 \ 1
1 151
2
1 224
1224
33
W/ 10/91
1 1
GW
Ct FAR
sw
4 - ft
NORTH
1 153
3
1 252
1253
34
10/10/91
1 1
GW
CI EAR
sw
4-8
NORTH
1 149
6
1410
14 1 1
3 b
10/1U/B1
1 '
<»W
CI EAR
sw
4 ft
NUR i H
1 1 b2
4
14'JO
143 1
3h
10/11/91
1
GW
OVFRCASi
NW/NE
b- H)
NOR 1 H
1148
b
1 Ib9
1200
37
10/11/9 J
1 1
GW
OVERCAST
NW/NE
5- 10
NORTH
1 151
2
1240
1242
3H
10/'1/9 1
1 1
GW
UVFRCAST
NW/Nf-
s-10
NOR i H
1 153
3
1330
39
10/11/91
1 1
GW
OVERCAST
NW/NE
5-10
NORTH
1 149
4
14 4 8
14 49
40
10/11/91
1 1
GW
OVERCAST
NW/NE
5-10
NORTH
1 152
5
1529
1b3U
4 !
10/11/91
1 1
GW
OVERCA'il
NW/NE
5 IO
NORTH
1 1 b4
2
1604
1605
42
10/11/91
1 1
GW
CVfcRCASI
NW/NE
5- IO
NORTH
1 13b
3
1751
1751
LtJ
EMISSION
EMISSION
MAXIMUM
MAXIMUM
TIME
TIME
STACK
STACK
MAXIMUM
I CiNi 1 I ON
UUK1NG
UUk 1 NE 1 AY .
PUSH.
i RAVfeL.
f-ORh
AM EH
A! BCX/JAMB
oes
SECONDS
SECONDS
SICONDS
IGNITION. %
IGNITION. %
iNiLRI ACE,
COMMLNIS
22
71
85
32
15
5
10
23
78
159
25
15
NO IGNITION
24
52
66
37
20
5
2b
57
92
124
35
20
20
2b
/b
1 12
137
3b
20
lb
27
G2
92
50
1b
20
2fi
3 1
126
73
45
25
10
29
ac
7 4
G 1
35
lb
5
30
42
' 12
86
25
20
10
PPORlFM WITH 1GN
3 1
25
l 1
b 1
2 b
1 :j
3 2
Gb
•i ;
' b
b
5
33
72
80
-14
20
10
TO
PRUDLCM WITH IGN
0-1
63
76
1 / 1
2 b
1b
2 b
3b
13
b«
56
15
5
IO
PROB W/EOX IN RACK
3fc
*jb
91
0
1b
b
IO
37
64
1 11
28
15
5
5
38
4 4
2 7 1
20
10
IGN I A IER W/f XPLSN
39
48
37
31
15
b
h
4D
37
4 9
54
10
10
O
4 1
40
52
25
15
5
0
42
32
10
10
10
0
\ LAKE WENT OUT
-------
KRfSS RtlX H 4Rt & PUSHING OBSERVATIONS 10:40 Tuesday. March 31. 1992 3
KRESS DEMONSTRATION PUOdtCT - BETHlfcHCM STEEL CORPORA I IDN
SPARROWS POINT, MARYLANU
WINO
f IMfe
OF
CUKt
OBSERVERS
WIND
SPEED
OBSERVER
OVLN
KRLVo
Qfr
K ARE
OR S
DATE
BATTFRV
INITIALS
WFATHFR
direct ion
MPH
1OCATION
PUSHED
BOX NO.
PUSH
IGNITION
43
10/12/91
1 1
GW
CLEAR
NW
h- IO
NOR 111
1 14B
5
1 132
1 132
44
10/12/91
1 1
GW
CLEAR
NW
5 IO
NORTH
1 1t> 1
2
12 12
1212
4b
10/12/yi
11
GW
CLEAR
NW
b- 10
NORTH
1153
3
1245
1245
46
10/12/91
1 1
GW
Ci EAR
NW
B- 10
NORTH
1 149
0
14 1b
14 1b
17
10/12/91
1 1
GW
CI FAR
NW
h- 10
NORTH
1 152
4
1446
1446
48
10/12/91
1 1
GW
CLEAR
NW
5- 10
NOW IH
1154
5
152 1
49
10/12/91
1 1
GW
CI FAR
NW
5- 10
NORTH
1 147
?
1727
1729
BO
10/12/9 1
1 1
GW
CLEAR
NW
5- <0
NORTH
1 135
3
1748
17bO
b 1
IO/12/9 1
1 t
GW
CI hAR
NW
5 10
NOR It t
117 1
6
18 17
18 19
52
10/13/91
1 1
GW
CLEAR
NW
S- 12
NOR III
1 MB
4
1 123
1 125
53
10/13/91
1 1
GW
CLEAR
NW
6 12
NORTH
1 Ibi
b
1 156
1 156
54
10/13/31
1 i
GW
CLCAK
NW
i) 12
NOR 1 H
1 1t»3
2
1232
1234
55
10/13/91
1 1
GW
CLEAR
NW
£ - 12
NORTH
1 149
3
M24
1426
ufe
10/13/9 1
1 t
GW
CLEAR
NW
6- 12
NOR 1H
1 152
6
1446
1446
57
10/ 13/9 1
1 1
CW
CLEAR
NW
6 12
NORTH
1 !•> 4
4
15 1b
15 16
50
10/13/91
1 I
GW
CLCAR
NW
6 12
NUKiH
1 147
5
17 16
17 IB
b9
10/13/91
1 1
GW
CLEAR
NW
6- 12
NOR f H
1 135
2
174 1
1742
<>C
10/13/91
11
GW
CLEAR
NW
6 12
NORTH
1 17 1
3
18 10
18 10
b 1
10/14/91
11
GW
CLEAR
SE
NORTH
1 MB
6
1 131
6?
If)/ 14/9 1
1 1
GW
CI FAR
SF
NORTH
1 lb 1
•1
1203
t 20b
63
10/14/91
1 1
GW
CI I AR
SE
NORTH
1 153
5
1246
1247
EMISSION
tMissroN
MAX JM11M
MAXIMUM
7 I ME
1 I ME
STACK
STACK
MAX IMUM
IGNITION
DURING
DURING
OPACITY
OPACITY
OPACITY
OELAY,
PUbH,
1RAVfcL.
BEFORE
AFTER
AT BOX/JAMB
OHS
SFCONDS
SECONDS
SFCONDS
T KNIT I ON. •/
4 IGNITION,
%
INTERFACE.
comments
•13
39
4b
33
15
IO
h
44
10
02
41
10
10
10
45
53
65
2?
IO
5
5
46
32
72
53
IO
15
5
47
43
53
3G
10
10
5
48
126
20
10
NO IGNJ]1UN
49
15
42
47
10
IO
10
5C
9
3B
40
25
25
5
b 1
8
50
35
10
30
C
52
12
96
32
5
5
10
53
22
87
42
10
' 5
10
54
9
4 £
18
10
5
10
55
6
3B
is 1
20
15
IO
50
1 1
53
27
15
5
20
57
9
4?
34
10
5
5
58
6
58
31
20
25
10
59
A
4G
20
15
10
b
60
7
62
36
10
5
b
61
48
132
15
b
NO IGNITION
62
12
13G
f 12
3 b
h
IC
63
6
12b
37
20
lb
IO
-------
liiS
64
6b
€6
67
66
69
70
71
72
73
74
7 b
76
77
/e
79
fiO
6 i
02
b 3
64
»HS
64
65
66
67
66
63
70
71
72
73
74
7'»
7f»
7 7
78
79
80
a i
62
b J
84
f 1 ME
or
LARE
NI 1 II
1422
1444
1508
17 18
1739
1800
1 1 18
1205
1229
1421
14b I
1514
17 15
17b4
18 14
1202
1 223
1427
1503
1 b24
KRtSS BOX FLARE & PUSHING OBSERVATIONS
KRESS HFMONSTRAT ION PROJFCT - BFlHl t HFM STECL CORPORATION
SPARROWS POINT. MARYtAND
10:40 Tuesday. Marcn
DATE
10/14/31
10/14/91
10/14/91
10/14/9 1
10/14/91
10/14/91
10/17/91
10/18/91
10/18/91
10/18/01
10/1B/31
10/18/9 1
*0/18/T 1
10/1ft/9 1
10/18/91
10/ 19/9 1
10/19/9 I
10/19/31
10/10/31
10/19/91
lo/19/91
IGNITION
DELAY .
SECONDS
5
10
13
1 1
5
14
23
15
2 1
0
4
11
7
' 1
I A
1 12
IB
9
0
II
COKE
BATTERY
EMISSION
TTMF
DURING
PUSH,
bt CUNDS
89
6?
74
65
92
1 17
8 i
38
S3
4 'J
104
4si
137
37
b I
125
103
ae
49
b2
GK
OBSERVERS
INI I IAL'.>
cw
GW
GW
GW
GW
GW
GW
GW
GW
GW
GW
GW
GW
GW
GW
GW
GW
GW
GW
GW
GW
EMISSION
T IMF
DURING
IRAVEL,
SECONDS
123
i 10
93
b 7
38
44
26
17
•re
6 1
rj
3 2
92
2b
36
402
6b
:;6#i
78
76
WLA1HCR
CLEAR
CLEAR
CLEAR
CLEAR
CI FAR
CLEAR
RAIN
CLEA3
CI FAR
CLEAR
CLEAR
CLEAR
CLEAR
CLEAR
CLEAR
CI FAR
CI EAR
CI FAR
CLEAR
CLEAR
CLEAR
MAXIMUM
STACK
OPACITY
BEFORE
ignii : :;n . 7
40
?h
20
25
20
lb
5
10
10
20
30
10
10
4b
40
2<>
3 b
20
20
WIND
DIRECIION
SE
SE
SF
SE
SE
SE
NW
NW
NW
NW
NW
NW
NW
NW
NW
SE
Sfc
Sf
SE
SC
SE
WIND
SPEED.
MPH
1b 20
10- 1b
10- 15
10 15
10- 1b
10 • lb
10 1 F>
10- 15
10- 15
h- 10
5- 10
5 10
b 10
5 10
b 10
20
5
lO
20
25
15
OBSERVER
LOCAI ION
NJk IM
NORTH
NORTH
NOR I H
NORTH
NORTH
NORTH
NOR IH
NORTH
NORTH
NORTH
NORTH
NORTH
NOR fH
NORTH
NORTH
NOR I H
NORTH
NORTH
NORTH
NORTH
MAXIMUM
STACK
OPACITY
AFTER
IGNITION. %
2 b
30
15
10
20
lb
5
10
MAXIMUM
OPACITY
AT BOX/wAMB
INItKFACE .
5
25
10
25
10
lb
o
5
e
o
5
10
o
5
10
b
10
5
20
5
OVEN
FUSHLU
1 149
1 1 b2
1 154
1 147
1 13ft
1 171
1 148
1 1f>1
1 153
1 149
1 1b?
i 154
1 13b
1 147
1171
I 1 43
1 151
I 153
1 149
1 1 b2
1 1 b4
COMMENTS
KRESS
UUX NO.
TIME
OF
PUSH
142 1
1444
1507
17 17
17 38
1759
1 147
1203
1228
14 20
1449
15 12
1713
17 b?
18 13
1 129
1200
1222
1425
1501
1523
PROBLEM W/OVN DOOR
-------
KRJ-SS ROX
MARE & PUSHING OBSERVATIONS
10
40 Tuesday
March
31. 1992
KRCSS
nCMONSTPATION
PROJECT DLTHLCHCM STLEI COKPORAllON
SPARROWS POINT,
MARYl
AND
TIME
WIND
TIME
OF
COKC
OBSERVERS
WIND
SPEED
OUbl-KVt-W
OVEN
KKtSS
OF
FLARE
GBS
DATE
BATTERY
INITIALS
WEATHER
OIRECTION
MPtl
L0CA1ION
PUSHtD
bOX NU
PUSH
1GN1I ION
8b
10/10/91
1 1
GW
CLEAR
SL
5-10
NORTH
1 135
3
1735
1736
Bfi
10/19/91
1 1
ow
C.t FAR
Si
5 - 10
NORTH
t 17 1
C
1758
1800
87
10/20/91
1 1
GW
CLEAR
NE
6-1?
NOR 1H
1 1b 1
b
1 148
1 149
88
10/20/9 1
1 1
GW
CI EAR
NE
6- 12
NORTH
1 148
~
1211
12 12
80
1O/20/11
1 1
GW
CLCAR
NC
C 12
NORTH
1 1 b!3
6
1238
124 1
90
10/20/9 1
1 1
GW
CLEAR
NE
6- 12
NORTH
1119
5
1449
I4b4
91
10/20/91
1 1
GW
CLEAR
NE
6 12
NORTH
1 1S2
3
1b 15
15 16
92
10/2O/H1
1 \
GW
CL F AK
Nfc
6-12
NORTH
1 154
6
1540
93
10/20/91
1 1
GW
CLEAR
NE
6- 12
NORTH
1 135
5
1750
1751
94
10/20/9i
1 1
GW
CLEAR
NE
6- 12
NORTH
117 1
3
1809
1813
95
10/21/91
1 1
GW
SE
b- 10
NORTH
1 148
6
1 143
1144
96
10/22/91
1 1
GW
CLEAR
SE
5- 10
N0R1H
1 148
6
1 t5 1
t 153
07
10/22/91
1 1
GW
CLEAR
SE
b 10
NORTH
1 1 v. 1
8
1222
98
10/22/91
1 1
GW
CLEAR
SE
5-10
NORTH
1 153
3
1250
1252
yy
10/22/91
f 1
GW
CLEAR
SE
5- 10
NORTH
1 149
6
J 501
1503
100
10/?2/9 1
1 1
GW
CLFAR
SE
5- 10
NORTH
1 17?
0
1550
1552
10 1
10/2 2/9 1
1 1
r.w
CI EAR
SF
b- 10
NORTH
1 152
3
1G26
1627
102
10/22/91
J 1
GW
CI FAR
SF
5-10
NORTH
1 135
5
1717
17 19
103
10/22/91
1 1
GW
CLEAR
SE
5 10
NCRTH
1 1 ^>4
G
17iq
1740
104
10/22/9 1
1 1
GW
CI FAR
SE
5-10
NORTH
1 17 1
8
175B
1800
iCb
10/23/91
1 1
aw
OVERCAST
SE
5-10
1 148
5
1 1 b3
1 1 b4
EMISSION
EMISSION
MAXIMUM
MAXIMUM
T IMC
TIME
STACK
stack
MAXIMUM
IGNITION
CURING
DURING
OPACITY
OPACITY
OPACITY
DtLAV.
PUSH.
TRAVEL,
BEFORE
AFTER
AT BOX/JAMB
ORS
SFCONOS
SECONDS
SECONDS
IGNITION. %
IGNITION,
«
INTERFACE,
COMMENTS
85
10
bi
*i7
15
10
10
86
7
78
62
10
b
0
87
5
67
51
b
b
5
88
7
4 b
bb
lb
5
10
By
38
117
46
40
5
0
90
4
48
39
10
5
0
9 i
8
56
52
io
5
«%
92
63
78
35
5
NO IGNITION
93
-J
50
3 1
30
10
10
04
32
1 14
4 2
30
'»
s
9 b
1 1
72
4 &
25
15
10
ah
1 1
VO
Hi 4
25
10
IO
97
fl
67
??ft
20
10
5
98
o
8b
126
20
1b
10
93
n
5rt
385
2b
15
5
100
7
78
147
15
20
10
101
13
63
1 I !
3b
15
10
102
46
75
31 \
bO
?n
IO
103
15
54
195
40
25
10
104
70
38
45
10
NO IGNITION
105
8
53
172
?o
2b
IO
-------
KRFSS BOX FLARE & PUSHING OBSERVATIONS 10:40 Tuesday. March 31, 1992 6
KWFSS OfMONSIRAI IC1N PROJECT - BC1HLCHEM STEEL CORPORATION
SPARROWS POINT. MARYLANO
T I Mh
WIND
I iME
OF
COKF
ORSFRVERS
WIND
SPfcfcD
OBSERVER
DVEN
KRESS
OF
F 1 ARF
DBS
DATF
F1ATTERY
initials
WEATHER
DIRECTION
MPH
LUCA1ION
PUSHED
BOX NO.
PUSH
IGNITION
106
10/23/91
1 1
GW
overcast
St
5- 1()
115 1
3
1222
1222
107
10/23/91
1 1
GW
OVERCAST
SL
5- 10
1 153
6
l?S>8
1300
108
10/23/9 1
1 1
GW
OVERCAST
SE
5- 10
1 149
8
1430
1431
109
10/23/91
1 1
GW
UVtKCAS1
Sfc
b- 10
1 172
5
1459
1501
1 10
10/23/9 1
1 t
GW
OVERCAST
SE
5- 10
f 152
3
1 s-j-j.
ih:>:j
111
10/23/91
1 1
GW
CI t AR
Sfc
5- 10
NORTH
1 135
G
17 17
17 19
1 12
10/23/91
1 1
G W
CLEAR
SF
5- 10
NOR i H
1 154
5
1751
1752
t 13
JO/23/9 »
1 1
GW
CI FAR
SL
5 lO
NORTH
117 1
3
18 12
1814
1 14
10/23/91
1 1
GW
Ci EAR
SE
5 10
NORTH
117 1
3
18 1?
18 14
1 15
10/24/9 t
1 1
GW
HAZY/OC
SE
5- 10
NORTH
1 14*
6
1 126
1 to
IO/24/9-.
1 1
GW
HAZY/OC
SL
S- lO
NOR 1 H
1 1b 1
5
1200
1 70?
1 17
10/24/91
1 1
GW
IIAZY/OC
SE
5 10
NORTH
11b3
3
1235
1236
1 16
10/24/91
1 1
GW
HAZY/OC
St
5- H)
NOR 1H
1 149
6
1433
1435
I 19
K)/i4/9 <
1 1
GW
HA/Y/OC
SE
b- lO
NORTH
117?
5
1459
1501
1 20
10/24/9 1
1 1
GW
HAZY/OC
SE
5- 10
NORTH
1152
3
1526
1530
1 2 1
Uj/j'l/'j 1
i 1
Gtf
CLLAR
SE
b - 10
NORTH
1 135
6
1740
1742
i 2 2
10/24/91
' S
GW
CLEAR
SE
b- 10
NORTH
1 154
5
1606
1806
123
10/29/91
11
GW
CLEAR
NE
8- 12
NORTH
1 148
3
1 149
1 150
W4
10/23/91
11
GW
CLEAR
NE
a-12
NORTH
115 1
5
1217
12b
10/29/91
1 1
GW
CLEAR
NF
8-12
NORTH
t 153
€
1310
126
10/29/91
1 1
GW
CI EAR
NE
8- 12
NORTH
1 149
2
1406
1 107
EMISSION
EMISSION
MAXIMUM
MAXIMUM
TIMF
TIME
STACK
STACK
MAXIMUM
IGNITION
DURING
DUPING
0PAC1TY
opacir v
OPACITY
DELAY .
PUSH,
TRAVEL,
BEFOHE
AF TER
AT BOX/JAMB
OBS
SECONDS
SECONDS
SECONDS
IGNITION. °
4 IGNITJUN.
%
INILRI ACt.
COMMfcNrs
106
16
64
246
?n
10
10
107
56
b2
158
20
to
5
106
2
78
137
45
30
1 <)
IGN LOST G8
srcs
109
2 1
57
153
35
15
10
110
5
62
209
30
20
lO
11 1
67
76
132
45
15
10
1 1?
15
55
f04
40
20
b
\ 13
24
ft 5
87
30
10
10
1 14
24
65
87
30
to
10
I 15
G2
j 15
20
10
NO IGNITION
t IS
17
57
36
15
to
!,
1 17
23
72
164
35
15
lO
1 IB
17
bb
V?
20
25
10
1 19
13
83
1M |
55
15
10
120
23
66
t?8
45
15
10
12 1
27
75
197
30
¦jo
5
122
lb
69
f 52
30
15
15
123
10
126
135
20
15
15
124
6
1 19
139
?0
10
lO
125
96
287
lb
10
NO IGNITION
I2S
13
132
2b?
20
15
10
-------
KRfcSS BOX
FLARE &
PUSHING
OBSERVATIONS
10
40 Tuesday
March
31. 199?
KRESS
ULM0NS1RAIiUN
PROJECI
- BtlHLEHtV
STEEL CORPORATION
jPAKWUWS POINT.
MARYLAND
TIME
WIND
TIME
Of
CO Kf
OBSERVERS
WIND
SPEFD,
UbSt WW R
OVEN
KRESS
or
FLARE
DBS
DATE
BATTERY
INITIALS
WEATHER
DIRECTION
MPH
LOCATION
PUSHED
BOX NO.
PUSH
IGNITION
127
1C/29/01
i t
GW
CLEAR
NF
8-
12
north
1 152
8
1422
1423
128
10/29/01
11
GW
CLEAR
NE
8-
12
NORTH
1 19 b
3
1 7 14
! 23
10/30/91
1 1
aw
CLEAR
NE
rj
20
NORTH
1148
3
1 128
130
10/30/91
11
GW
CLEAR
NE
15
-20
NORTH
1 151
2
1202
1203
131
10/30/91
1 1
GW
Cl EAR
NE
1 b
-20
NORTH
1 153
8
1229
1230
132
1O/30/91
1 1
GW
CLEAR
NK
15
-20
NORTH
1 149
3
14 16
14 17
133
10/30/91
11
GW
CI fcAR
NF
1b
-20
NOR 1 H
1 172
5
1 134
1435
134
10/30/91
1 t
GW
CLEAR
NF
15
-20
NOR 1 H
1 152
G
1450
1451
135
10/1i/ni
1 1
GW
CLEAR
NE
ib
20
NORTH
1 148
2
1 159
136
iO/31/91
1 1
GW
CI far
NE
15
20
NORTH
1151
3
1227
1228
137
JO/3 1/91
1 1
GW
01 b Aft
m
15
20
NOR 1 H
1 153
b
12 4y
12bO
138
1
b
137
ft
07
;• i "1
25
10
5
138
1?
82
2 '7
15
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!j
133
7
/*>
'J 6
2Q
10
IO
14'J
a
1 1 1
' 7 1
25
15
b
14 1
5
56
4 2
lb
ro
5
142
3
63
t>4
1 5
15
5
143
5?
' 1 3
IO
NO IGNI 1 ION
144
13
55
14 1
20
10
0
14b
1 1 7
48
176
35
b
IGN DURING
INAVEL
146
67
57
72
30
5
5
IGN DURING
TRAVEL
147
14
bd
4 2
15
10
5
-------
KRESS BOX FtARE & PUSHING GBSFRVATIONS 1O:40 Tuesday, March 31, 1992 a
KRFSS DEMONS1RA1 I ON PROdfCT - BETHLEHEM STEEL CORPORATION
SPARROWS POINT, MARY!AND
TIME
WIND
TIME
OF
CCML
OBSERVERS
WINU
SPLLD
OUblKVLK
OVEN
KRESS
Of-
H ARF
OBS
DATE
BAi ifcHY
INI11ALS
WEATHER
DIRECTION
MPH
LOCATION
PIJSHFD
ROX NO
PIJSH
IGNITION
148
11/06/01
1 1
r.w
CLEAk
sc
6 12
NORTH
1 1b 1
8
1 1 bb
149
11/06/91
1 1
GW
CLEAR
SF
6 12
NORTH
1 153
3
1230
123 1
IbO
11/C6/91
1 1
GW
CLEAR
SE
6 12
NORTH
i 149
2
14 13
14 14
151
I 1/OS/31
1 1
GW
CLEAR
SE
6- 12
NORTH
1 172
5
1435
152
11/06/91
1 1
GW
Cl FAR
SE
6- 12
NORTH
1 152
3
1 4 bfl
iiDy
151
11/07/91
1 1
GW
OVERCAST
NF/SF
4 B
NORTH
1 148
2
1147
1 14ft
154
11/07/91
1 1
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0VFRCAS1
NE/SE
•1 8
N0R1H
1 lb 1
5
1 ? 10
17 12
155
11/C7/91
1 1
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GVtRCAS 1
NE/SE
4 8
NOR IH
1 153
3
124 1
1 h6
t1/07/91
1 1
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0VFRCAS1
NF/SE
4-8
NORTH
1 149
6
14 16
14 1 7
1b7
11/OV/31
1 1
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OVFRCASI
NF/Sfc
4-8
NORTH
1 172
2
1445
1447
159
11/07/91
1 1
GW
OVERCAST
NE/SF
4-8
NORTH
1 1 52
b
1514
15 15
153
1 1/12/9 1
1 1
RF A
OVFRCAST
NW
7 - 10
NORTH
1 148
4
1 ! 39
1 14 1
160
1 1/12/9 1
1 1
RF A
OVERCASI
NW
7- 10
NORTH
1 15 1
8
1209
1210
1 (i 1
1 1/ «?/3 1
1 1
Ub A
OVERCAST
NW
7- 10
NORTH
1 1 53
3
1240
1 24U
If*?
11/12/91
1 1
Rr a
OVERCAST
NW
7 10
NORTH
1 1 49
4
1440
144 1
163
11/12/91
1 1
RE A
OVERCAST
NW
7- 10
NtlHIH
1 1 12
8
1500
1501
lui
1 1/ 12/d 1
1 1
RE A
nVFHCAbl
NW
/ 10
NORTH
1 152
3
1520
15? 1
i 05
11/13/9 1
1 1
Rl-A
CLEAR
WF ST
5- 10
NORTH
1 1 48
6
1 145
1 140
1 66
1 1/13/9 1
1 1
RE A
CI FAR
WFSI
5- 10
NORTH
1151
5
1209
1211
107
11/1J/T 1
1 1
REA
CLEAR
WCST
5 10
NORTH
1 1b3
B
1239
1240
1 03
11/14/91
1 1
RCA
clear
WES!
5
NW
1 14B
2
1 130
113 1
FMISSION
EMISSION
MAXIMUM
MAXIMUM
1 1Mb
I IME
STACK
STACK
MAXIMUM
1GN1I ION
DURING
DURING
OPACITY
~ MACI 1V
OPAL I IV
OElAY.
PUSH.
INAVH .
dtl-ONt:
AFTER
AT BOX/JAMB
UBb
SfcCONDb
btCUNDS
SECONDS
iGNiliON, %
IGNITION,
%
INILKFACE,
COMMENTS
148
64
1 bb
2 b
10
NO IGNI1 ION
149
I 1
52
56
15
5
O
150
G
67
4?
15
5
10
151
15
54
135
10
5
10
152
a
66
b 1
20
10
10
153
9
1 iy
75
20
15
5
154
13
98
Bb
20
lb
10
1 bb
130
48
20
0
NO IGNIiION
156
15
127
54
15
10
5
157
b
131
4 b
10
10
IO
lb 3
4
103
20
15
IO
159
35
2^0
10
5
15
160
40
250
15
5
15
lb 1
30
24C
10
5
5
162
35
36 O
15
5
5
163
76
ItfC
10
5
b
164
35
lac
b
5
5
165
40
90
15
5
5
166
25
7C
10
b
5
167
35
15
b
1fed
58
106
io
5
20
-------
DBS
169
170
171
172
173
174
t /S
176
177
178
179
iao
181
132
?83
184
•.85
1 Bo
187
188
189
OBS
169
170
1 7 1
172
173
1 74
175
176
177
170
l I'J
180
Id 1
182
183
184
18b
18b
187
188
139
KRFSS ROX FlARt & PUSHING OBSERVATION?- 10 40 Tuesday. M.irch 31. 1902 9
KRESS DFMONSTRATION PROJECT BFTHlEHEM STEEL CORPORATION
SPARROWS POINT, MARYlANf)
DATE
11/14/91
1 1/14/91
1 1/14/91
1 1/11/91
11/14/91
11/13/91
1 1/?S/9 t
1 1/ 19/91
11/ 19/91
1 1/19/91
1 1/19/91
1 1/19/9 I
11/ m/qi
1 1/ in/:ll
' ? /?C/3 I
1 1/20/91
1 1/20/~ I
1 /20/9 1
1 i/2C/y1
11/20/91
1 1/20/91
COKt
BATTfRY
ObStKVtRS
INITIALS
RLA
REA
REA
Rl A
REA
UW
GW
GW
GW
GW
GW
GW
aw
GW
R!IA
^E A
3C A
Rt A
RLA
RLA
GW
CLEAR
CLEAR
CLtAR
CLEAR
CLtAR
CLEAR
CLEAR
CLEAR
CLtAR
CLEAR
CLEAR
CA FAR
CLEAR
CLEAR
CLLAR
CI EAR
LI FAR
CLEAR
CLtAR
CL EAR
CLEAR
WIND
DIRECTION
WEST
WES I
WtSI
WEST
WEST
St
St
SE
SE
St
SF
SF
SE
SE
SW
sw
SW
SW
sw
sw
sw
w r no
SPEFD.
MPH
0 10
6- 10
6 - 10
G 10
6- 10
6- 1(3
6- iO
G 10
G 10
1 U - 1 b
10- lb
10 15
10- vj
10-1b
10- 1b
IO 15
CJHSfrKVtR
LOCATION
NW
NW
NW
NW
NW
NOR i H
NOR IH
NOR TH
NORTH
NfiR IH
NORTH
NORTH
NORTH
north
NORTH
north
NORTH
NCJR f H
NOR I H
NOR I H
NORTH
OVEN
pushfo
1 1i>1
1 153
1 149
1 172
1 152
1 148
1 151
1 153
I 149
1 172
1 152
1 135
1 1 b4
1171
1MB
1 151
I 10 J
II 49
1 172
1 152
1 1 35
KRESS
ROX NO.
6
5
2
6
5
S
5
6
4
8
7
1
2
TIME
OF
PUSH
11-19
I 2G9
1505
153 1
1555
1320
1337
1402
f 4?0
1436
14b6
1515
10
1304
1320
13-13
1403
1428
1502
11 Mf
OF
FLARE
JGNITION
i 150
12 IO
150^
153?
1556
1322
1403
1422
1438
1459
1516
153
1307
1322
f 311
1404
1429
1503
1GNi11CN
DELAY.
SFCONOS
a
19
1 J
EMISSION
! I ME
DURING
PUSH.
SFC.ONDS
46
4 7
4(>
37
15
52
64
7b
b j
by
17
8b
:-$Ci
EMISSION
I 1 Mb
DURING
TRAVFI ,
SECONDS
256
14b
300
24Q
12(i
13b
10
j j r
5d
ibj
2-38
c 7
o!)
MAXIMUM
STACK
OPACITY
RFFORF
IGNITION, %
\\i
lb
40
30
15
'0
5
1b
JO
JO
10
30
MAXIMUM
STACK
OPACITY
AFTFR
IGNITION, %
b
b
5
15
10
20
10
20
:> n
10
15
MAXIMUM
OPACITY
AT BOX/JAMB
INTFRFACF,
20
10
25
1b
10
COMMENTS
PUSHED BE! ORE 1300
NO IGNITION
49
23
15
74
2-10
99
107
156
1 7 1
22b
20
10
20
10
10
20
5
15
10
5
30
20
10
10
10
5
10
-------
KRESS BOX I LARt & PUSHING OBSE RVA; i UNb lO; 40 Tuesday. Mar«:h 31, 1992 10
KRFSS DFMONSTRATION PROJECT - BfrTHLEHEM STEEL CORHORATION
SPARROWS POINT, MARYiAND
TIME
WIND
TIMC
OF
COKf-
OBSFRVFRS
WINO
SPEED,
OBSERVER
OVLN
KRESS
OF
hi ARfc
OBS
DA I b
BATTERY
INITIALS
WCAThCR
DIRECTION
MPH
lOCA!ION
PUSHfcO
BOX NO.
PUSH
IONIriUN
190
1 1/20/91
t 1
GW
CLEAR
SW
10- 15
NORTH
1 154
1
1b39
1b40
101
1 I/20./91
1 1
CW
CLEAR
SW
lO - lb
NOW IH
117 1
2
1558
1600
192
11/21/91
1 1
GW
CLR/OCST
SE
4 a
NORTH
1 148
3
1253
12b4
193
11/21/31
1 1
GW
CLR/QCST
sc
4 a
NURIH
1 151
9
13 15
iniB
194
1 1/21/91
1 1
GW
CLR/OCST
SE
4-0
NORTH
1 153
5
1332
1333
195
11/21/91
1 1
GW
01R/OCST
bfc
4 8
NORTH
1 149
6
I3b3
1354
196
1 1/21/91
t 1
GW
CLR/orsi
SE
A 8
NUKIH
117 2
4
14 1 1
1412
197
1 1/2 1/91
1 1
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CIR/OCST
SF
4 Q
NORTH
1 152
6
1428
1 129
198
1 1/21/91
1 1
GW
CLR/OCST
SE
4-8
NORTH
1 135
7
1553
1 b54
190
1 1/2 1/9 1
1 1
GW
CLR/OCST
St
*3 8
NORTH
1 1b4
1
162?
1623
200
1 1/2 1/91
1 1
GW
CLR/OCSI
S€
4-8
NORTH
117 1
2
1643
1044
201
1 1/22/91
1 1
GW
UC/RA1N
SOUTH
10- 1b
NORTH
1 148
3
1255
1 257
202
1 1/22/91
< 1
Gw
OC/RAIN
SOUTH
to- 1b
NORTH
1 1b1
9
13 12
1314
203
1 1/22/51
< 1
GW
OC/RAIN
SOUTH
10 15
NORTH
1 153
b
133 1
1313
20-
1 1/22/9 1
1 1
GW
OC/RAIN
SOUTH
10- lb
NOR 1 H
1 149
6
1352
1353
L'O'j
1 1/22/91
1 1
GW
OC/RAIN
SOU H
10-15
NORTH
1 172
4
14 14
1416
206
1 1/22/9 1
1 1
GW
OC/RAIN
SOUTH
10 15
NORTH
1 152
8
144 1
144b
2U7
1 1/22/91
1 \
Gw
OC/RAIN
SOUTH
10 1b
NUN TM
1 135
7
1537
lb 38
20fl
1 1/22/91
1 1
GW
OC/RAIN
SOU M
10 15
NORTH
1 154
?
1623
1623
209
1 1/22/91
1 1
Gw
OC/RAIN
SOUTH
10- 1 h
NORTH
1171
3
1G4 1
2 10
1 1/23/91
1 1
G*
CLtAR
SE
5 10
NOR I H
1 1*48
7
1332
1333
LMlSSION
EMISSION
MAXIMUM
MAXIMUM
1 1M t
I XML
STACK
STACK
MAXIMUM
IGNI1ION
DURING
DURING
OPACT TV
OPAClTv
OPACITY
UtLAV ,
PUSH,
I RAVEL,
BEFORE
AFTER
A
BOX/JAMB
CBS
SFCONDS
SFCONOS
SECONDS
IGNI I ION. "/
i IGNITION,
% INT f RFACE,
C'.UMMt- NTS
iyo
«J
76
<13
10
10
5
10 1
3
52
195
10
25
10
192
3
66
139
20
10
20
193
2
52
152
10
15
b
194
7
60
167
5
20
in
195
b
85
15?
30
25
15
196
0
82
14G
10
15
lb
197
0
93
i e f
1b
20
15
198
12
82
1 u>
2 b
10
20
ia9
A
77
i 2G
i5
10
b
200
5
69
106
10
20
20
201
lO
7 ft
\es:
20
* b
0
20?
3
86
201
20
20
10
203
17
76
227
25
'JO
5
204
5
70
19o
25
30
2b
205
o
83
pnft
10
20
20
206
240
68
2 1
30
15
10
20?
9
81
142
40
20
lO
208
5
65
1S 1
15
20
5
209
TOO DARK TQ
SEE
2 10
7
6b
142
?C
10
5
-------
KRESS GO*
blARt A PUSHING DBS
EPVATJONS
10-" 40 3 uejjfJ.Hy'
Ma rch
31, 1932
KRESS
DCM0NSTRA1 ION
PWnjfcC! - BETHLEHEM
STEEL CORPORATION
SPARROWS POINT.
MARYLAND
T I ME
WIND
TIMF
OF
COKF
OHSE-RVLKS
WIND
SPEFO.
UUSLRVtR
OVLN KRESS
OF
Fl ARE
QBS
DATE
HATTERY
INITIALS
WlATHER
DIKEC rION
MPM
LOCAl1QN
PUSHtO BOX NO.
PUSH
1GNT1 I ON
2 1 1
i1/23/31
1 1
GW
CLEAR
bt
b 1
1 1/24/91
1 1
GW
clear
NW
8-12
NORTH
1 1 b4 2
1507
1508
227
1 1/24/91
1 1
GW
CLtAR
NW
b-12
NORTH
1171 7
1631
2 2ii
1 1/25/9 1
1 1
SBH
CLE. AW
NW
15-20
NORTH
1 148 7
1304
1305
2 29
1 1 / 2 b / 9 1
1 1
SBP
Cl PAR
NW
1 h - 20
NORTH
1151 3
132 1
230
1 1/25/91
1 J
SHP
clear
NW
15-20
NORTH
1 153 3
1337
1339
>3 1
t 1/25/91
1 1
sap
CLCAR
NW
1b 'JO
NORTH
1149 5
1359
f^MI SSI ON
tm ssiom
MAXIMUM
MAX IMUM
1 1 ME
I 1 ME
STACK
STACK
MAX T MUM
IGNITION
OURING
DORING
OPACIIY
OPACITY
OPAOi Y
DELAY,
PUSH,
IKAVEL.
BEFOat
Af-TEK
AT SOX/JAMS
UBS
bfCCJNOS
SECONDS
SECONDS
1UN1IIUN. *1
IGNITION.
% INTERFACE.
COMMUNIS
:> 11
1 5
73
134
30
15
5
2 12
5
6?
1 19
IS
15
10
2 13
3
5a
97
15
15
b
2 14
5
5 1
25
15
JO
2 15
2
96
nr.
20
15
fi
2 Ifc
9
7 J
184
25
20
15
2 17
12
43
f f5
15
10
5
2 18
100 DAKK 10 SFF
2 19
a
ft 2
125
30
IS
b
220
•1
ba
9 1
1 G
10
b
22 1
14
18
2 4
5
b
0
222
9
5G
1 2J
?o
20
b
1?
3 1
5-1
'¦»
b
' b
224
fi
12
0
10
b
b
225
h
18
4 1
5
5
226
9
22
33
b
5
5
221
5
Jti
15
b
5
5
220
(j
SO
40
25
5
25
229
7 1
203
40
NO IGN1fI ON
230
20
107
H5
20
10
10
23 t
5
108
14f)
15
'j
b
-------
KRESS BOX f I A RE & PUSHING OBSERVATIONS
KKfciS DLMONSIRAIION PROJECT - BETHLEHEM STEEJ CORPORATION
SPARROWS POTNT. MARYl ANO
10:40 Tuesday, March 3!, 1992 12
>
1
00 S
232
233
234
235
236
237
?3H
239
?40
24 1
242
243
244
¦J A b
246
24 7
248
243
2 SO
25 '
uos
232
233
234
235
236
237
23fl
2 39
240
24 t
2 4 2
243
244
2-15
24 6
24 7
246
249
250
251
UAI E
1 t/25/S 1
1 1/25/91
11/25/91
1 1/25/91
1 1/25/91
1 1/25/9 I
1 1/25/91
I 1/25/91
1 1/25/91
I 1/25/91
1 1/25/01
1 1/25/91
I 1/24j/J 1
i 1/25/91
I 1/25/9 1
I 1/26/91
11/26/01
I 1/26/91
1 1/20/9 1
I 1/28/9 I
IGNITION
OH AtC .
SECONDS
8
4
23
2
a
5
O
1-1
COKE
BAIIfcRY
CMI55 ION
J Ml
DURING
JSH .
SECONDS
9 I
66
7S
1 10
70
83
52
54
'JO
67
7 4
109
00
go
2ft
57
72
00
WIND
TTMF
OBStRVLRS
WIND
SPEED,
OKSFRVFR
OVEN
KRESS
OF
INI 1I AL5
WhA!HfcK
DIRECTION
MPH
IOCATION
PUSHFD
BOX NO.
PUSH
NBP
CLEAR
NW
*.5 20
NORTH
1172
6
14 17
GW
Ct LAR
NW
10 15
NUKIH
1 148
7
1304
GW
CLtAR
NW
10- 15
NORTH
1 15 1
3
132 1
GW
CLtAR
NW
10- 15
NORTH
1 153
9
1337
uw
CLLAR
WW
tC- 15
NORTH
1 149
l>
1359
CiV#
CI EAR
NW
KJ- 15
NORTH
1 17?
r.
14 17
GW
CI FAR
NW
10- 15
NORTH
1152
4
1448
(iW
CLEAR
NW
10 15
NORTH
1 135
8
15 12
GW
CLEAR
NW
10- 15
NUR I H
1 154
2
1539
GW
CLEAR
NW
10 - 15
NORTH
117 1
RJA
CLEAR
NW
10-20
NOR FH
1 148
7
1304
R JA
CLEAR
NW
'0-20
NORTH
1 15 1
3
132 1
RJA
CLEAR
NW
10 20
NORTH
1 153
9
1337
RJA
CI TAR
NW
*0-20
NOR I H
1 149
5
1359
RJA
CLEAR
NW
10-20
NORTH
1 172
6
14 17
Gw
CLEAR
NW
a-12
NOR III
1 148
GW
CI FAR
NW
a 12
NORTH
1 151
9
1302
GW
CLEAR
NW
8- 12
NORTH
\ 153
6
1313
GW
CI 1- AR
NW
8-12
NOR in
1 143
4
1325
GW
CLEAR
NW
a-12
NORIM
1172
e
1337
EMISSION
MAXIMUM
MAXIMUM
T IME
STACK
STACK
maximum
DURING
OPAL I I V
UPAC11V
QPACITY
1 RAVcL.
BEFORE
AFTFR
AT
RCX/JAMR
SECONDS
1 GNU ION. °/
KiNI 1 ION.
% INTERFACE,
COMMENTS
165
20
10
tO
43
20
10
25
200
40
NO IGNIIION
85
15
10
to
152
10
10
10
175
15
1?
10
35
20
10
b
7 5
io
10
10
FARi i IGNITION
2 1
5
*
TOO DARK 10
SLt
40
i'5
5
2L1
2 oo
40
NO T GNI~I ON
83
10
10
15
ir.O
IS
10
1 70
15
10
10
PUSHED BEFORE 1300
1'tS
10
5
NO IGNITION
1-7
35
10
5
129
20
20
15
4 7
35
10
20
T I ME
OF
FLARE
IGN1I ION
1118
1305
1339
1400
14 18
1449
1 b 1 3
1540
1305
1339
14QO
14 18
1314
1327
1338
-------
KRESS BOX FLARE: & PUSHING OBSERVATIONS
KRESS DEMONSTRATION PROJECT - BETHlEHEM STELl CORPORA"ION
SPARROWS POINT, MARY1ANH
10:40 Tuesday, March 31, 1992 13
CCKE
~ATE BATTERY
OBSERVERS
INITIALS
WEATHER
WIND
DIRECTION
w f ND
SPErn.
MPH
035CRVl*
LOCATION
OVEN
PUSHED
KRESS
BOX NO.
TIME
or
PUSH
TIME
OF
FLARE
I6NITION
252
253
11/26/91
1 1/26/9 I
1 1
1 1
GW
QW
CI FAR
CLEAR
NW
NW
8-12
8-12
NOR 1H
NOR I H
1 1 1j2
1 1 b4
1347
1400
13-19
IGNITION
UkLAY ,
SECONDS
EMISSION
( I ME
DURING
PUSH.
SECONDS
EMISSION
I IMF
DURING
IRAVtl.
SECONDS
MAX1MUM
STACK
OPACITY
BL FORE
IGNITION.
MAXIMUM
STACK
OPACITY
Ai- I £ R
IGNITION.
MAXIMUM
OPACITY
AT BOX/JAMB
INTERFACE.
COMMENTS
252
253
17
62
67
08
126
25
10
20
10
40
NU IGNITION
>
1
NJ
-------
19!
:iw
iCl
~TN(
fEL
45
lO
35
40
0
5
45
0
o
o
o
0
o
15
IO
o
10
10
to
55
45
20
25
15
45
85
70
bb
25
70
20
1b
25
1b
20
3b
20
15
GO
2b
45
55
15
25
IO
5
2b
15
10
45
30
PUSHING EMISSIONS CONTROL uA1 A 11/12 HAT f F R Y
KI DC DFMONSTRAT ION PROJECT - BFTHLEHFM STEEl CORPORATION
SPARROWS POINI, MARYiANO
10.48 Tuesday, March
EMISSIONS
EMISSIONS
TOT At
MAX 1 Ml
EMISSION
DJW1NG
DURING
EMISSION
0PAC11
nROCavtRS
WIND
W i NO
OBSERVER
CONTROL
CVLN
I I ML ur
PUSH
TRAVEL
T IMF
our i n<
INITIALS
WtATnER
DltfECI ION
SPELU
LOCATION
SYSTEM
PUSHED
PUSH
SECONDS
seconds
SECONCS
PUSH.
gw
CL FAR
WEST
15 20
NC
SHENANGO
1 1G7
12 12
105
42
14 7
6b
G W
CLEAR
WEST
15 20
NE
CHENANGO
1207
1224
102
64
166
10
GW
CLtAR
WES I
1b -20
NL
SHENANGO
1217
1238
12 2
41
165
65
GW
CLEAR
WhS I
1b-20
NE
SHENANGO
1237
1255
102
61
163
85
GW
CLEAR
WEST
15-20
NE
SHENANGO
1 247
132b
440
46
186
35
CW
CI FAR
WFST
15-20
NF
SHENANGO
1257
1 34G
65
4 1
106
30
GW
CI EAR
WEST
15 20
NC
SHENANGO
1267
1402
13b
51
186
100
GW
QC/RAIN
NE
10- lb
NL
SHI-NANGO
1 125
12 17
73
84
157
35
GW
OR/RAIN
NE
10- 1f>
NF
SHENANGO
1205
1545
75
6 1
136
20
GW
OC/RAIN
NE
10- 15
NF
SHENANGO
12 lb
1252
CO
71
139
25
gw
OC/RAIN
NE
10 tb
Nf
5* ItNANGO
122b
1 3 ? f.
4b
VH
123
SO
GW
0C/RA1M
NE
10- lb
NE
SHENANGO
123b
1333
5-1
67
121
0
GW
UC/KAIN
Nfc
10- 1b
NL
SHENANGO
1245
1344
67
53
120
1b
GW
OC/RAIN
NE
10 15
NF
SHENANGO
i 127
1407
4 (j
li'j
1 1 1
40
GW
flC./RAlN
NI-
10- 15
NE
SHENANGO
1 147
14 1C
89
1 13
202
2b
GW
OC/RAIN
NE
10- 15
NF
SHh NANGO
1 207
142b
49
b9
138
1b
GW
OC/RAIN
NL
IO- 15
NC
SHLKANGO
12 17
1136
56
7 1
127
4b
GW
OVtRCAS I
SL
10- 15
NORTH
CHEMTCO
1208
1 1 36
6 1
74
135
30
GW
OVERCAST
SE
10- lb
NORTH
CHEMICO
1248
12 10
70
52
122
100
GW
OVERCAST
SE
10 15
NORTH
CHEMICO
1258
1224
49
It 3
102
8b
GW
OVERCAST
SE
10- lb
NORIH
CHEMICO
126H
12JB
bi
29
83
65
GW
UVtKCAS1
St
10- 15
NORTH
CHEMICO
112 1
1252
76
AG
162
bO
GW
DVFRCAST
SE
10- 15
NOPTH
CHFMTCO
113 1
1302
58
121
169
ao
GW
OVERCAST
SE
10- lb
NORTH
CHEMICO
1 10S
1315
63
6b
128
bb
GW
ovlwc a*o r
St
10" !5
NORTH
CHEMICO
1 1b 1
13130
76
7 1
147
75
GW
OVfcRCASI
SE
10- 15
NORTH
CHFMTCO
117 1
1339
7 1
86
157
1 GO
GW
OVERCAST
SE
10- 15
NORTH
CHEMICO
1 101
13b 1
fee
67
135
100
GW
OVFRCAST
SF
10- 1b
NORTH
CHEMICO
1201
1402
42
48
90
100
GW
ovepcast
NORTH
CHEMICO
117 1
1314
57
61
118
75
GW
OVLRCASI
NORTH
CHLM1C0
1201
1 324
84
b8
142
5 OO
GW
OVERCAST
NORTH
CHEMICO
12 11
13 30
7?
49
1 2 1
100
GW
OVLKCASI
NORTH
CHEMICO
122 1
134b
8 1
45
126
100
GW
OVERCAST
NORTH
CHFMICO
123 1
1 3b9
4 3
34
77
100
GW
RAIN
NW
NORTH
SHrNANC.0
1208
1 122
73
48
121
fto
GW
RAIN
NW
NOR 1 H
SHENANGO
1226
1 134
47
20
73
35
GW
MA IN
NW
NORTl 1
SHCNANGO
1 238
1142
B3
22
10b
100
GW
RAIN
NW
NOR I H
SHENANGO
1 2'18
114 9
9 1
17
108
75
GW
RAIN
NW
NORTH
SHENANGO
12-5R
1 1b7
7q
25
104
100
GW
OVLRCASI
NW
10- lb
NUR f 11
SHLNANGO
1 238
1 144
48
20
77
85
GW
OVERCAST
NW
10- 15
NORTH
SHENANGO
4
1 \ 5 3
4 1
33
7 4
100
GW
overcast
NW
10- 1 b
NUR 1 H
SHENANGU
1 256
1215
44
31
7b
7 b
GW
OVERCAST
NW
10 15
NORTH
SHENANGO
1 ?r>H
1 2? 4
4 2
2 2
64
100
GW
OVERCAST
NW
10- 15
NORTH
SHENANGO
1101
1324
62
112
174
30
GW
0VLRCA5T
NW
10-15
NORTH
SHENANGO
112 1
1338
39
107
146
0
GW
OVERCAST
NW
10- 15
NORTH
SHENANGO
1 131
1354
67
7*
145
45
GW
OVERCAST
NW
10- lb
NORTH
SHENANGO
1 151
1403
58
73
131
15
GW
UYLRCASI
NW
10- 15
NORTH
SHENANGO
1 17 1
14 12
50
76
135
100
GW
OVERCAST
NW
10- 15
NORTH
SHENANGO
1201
1429
65
37
102
75
GW
CLEAR
NW
10 15
NORTH
CHEMICO
1228
1331
53
39
92
45
SBP .
OVERCAST
NW
10
Nh
SHENANGO
1206
1 136
58
48
106
100
SBP
OVFRCAST
NW
10
NF
SHENANGO
1216
1 147
60
58
118
100
-------
PUSHING t MISS J ONS CONTHOl OA 7 A 11/12 B
K I DC DEMONSTRATION PROJECT - HfclHLfcHfcW S f E fc I
SPARROWS POIN1. MARYLAND
LM1b 51ON
OBSERVERS
WIND
WIND
OBSERVER
CONTROL
OVEN
11 me in
0B6
DATE
INITIALS
WtAIHLR
DIRECTION
SPEED
LOCATION
SYSTEM
PUSHED
PUSH
52
0-1/09/91
SEP
QVLKCAS1
N¥f
10
Nt
SHENANGO
1 226
1206
53
04/09/91
SbP
UVERCAS1
NW
1C)
NE
SHENANGO
1236
1220
51
C4/09/91
SEP
OVERCAST
NW
10
Nf
SHFNANC.n
1 24G
i ?ru
b'j
01/09/91
SBP
OVERCAST
NW
10
NF
SHENANGO
1256
124 1
56
04/O9/91
SBP
OVFROAST
NW
10
NF
SHFNANGO
i a
1301
5?
04/09/91
SBP
OVFRCAST
NW
10
NF
SHENANGO
1200
1311
58
04/09/91
SRP
OVERCAST
NW
10
NE
SHENANGO
12 18
1320
59
04/09/91
SBP
OVERCAST
NW
to
NE
SHENANGO
1238
1340
GO
04/10/91
SBP
CLEAR
NW
15 20
NE
SHENANGO
124 1
1 121
61
04/10/91
SEP
CLEAR
NW
15-20
NE
SHENANGO
1 108
114 1
62
04/10/91
SbP
CLEAR
NW
15 20
Nt
SHENANGO
1206
1 151
63
04/10/91
SBP
CLEAR
NW
15-20
NE
SHFNANGO
1216
1209
64
04/10/91
StiP
CLEAR
NW
15-20
NF
SHFNANGO
1226
12 16
65
04/10/91
SBP
CI FAR
NW
15-20
NF
SHENANGO
1 23G
122G
66
04/10/91
SBP
CLtAR
NW
15-20
NF
SHFNANGO
1246
1240
67
0 4/ 10/91
SliP
CLEAR
NW
15 20
NF
SHENANGO
1 143
1257
r,R
04/10/91
SBP
CLEAR
NW
15 20
Nt
SHENANGO
1 168
1311
6 9
04/10/91
SBP
CLEAR
NW
15-20
NE
SHENANGO
1208
1320
70
04/ lb/9 1
gw
R A 1 N
St
6- 12
NOR IH
SHENANGO
1 126
1144
7 1
04/15/91
GW
RAIN
SE
6 - 12
NORTH
SHENANGO
12O0
1204
72
04/15/91
GW
RAIN
SE
6-12
NORTH
SHENANGO
1216
1223
73
04/15/31
GW
RAIN
SL
6-12
NOR IH
SHENANGO
1226
1228
74
04/15/91
GW
RAIN
Sfc
6- 12
NORTH
SHENANGO
1236
1246
7 b
04/15/91
GW
RAIN
SE
6-12
NORTH
SHENANGO
1246
1259
7G
04/15/91
GW
RAIN
SF
6 • 12
NORTH
SHENANGO
125G
1309
77
04/15/91
GW
RAIN
SE
6 12
NORTH
SHENANGO
1148
1338
76
04/15/91
GW
RAIN
SE
6- 12
NORTH
SHENANGO
120B
1354
79
04/15/91
GW
RAIN
SE
6 12
NORTH
SHENANGO
1246
1403
80
04/ 16/91
GW
CLEAR
NW
15-20
NOR I H
CHEMICO
1244
1 125
81
04/10/91
GW
CLEAR
NW
15-20
NORTH
CHFMICO
1 126
1 14 1
8?
04/16/91
GW
CI FAR
NW
15-20
NORIH
CHEMICO
1 1 46
1204
83
04/16/91
GW
CLEAR
NW
15 20
NORTH
CHEMICO
1206
1212
84
04/ 16/9 1
GW
CLEAR
NW
15-20
NORIH
CHEMICO
12 16
1229
8b
04/16/91
GW
CI EAR
NW
15-20
NORTH
CHEMICO
1226
1244
86
04/ 16/9 1
GW
CI FAR
NW
15-20
NORIH
CHEMICO
1236
1300
87
04/ !f./9 S
GW
CLEAR
NW
15 20
NOKIH
CHLM1C0
12 46
1313
88
04/ 16/91
GW
CLEAR
NW
15-20
NORTH
CHFMICO
1 109
131?
89
04/2 4/9 1
GW
4AIN
SI
8-12
NORIH
CHEMICO
1206
1 248
on
04/?4/9 1
Gw
^6 IN
<1
H 1 J
NOW 1 H
CHtMJCO
12 16
1 JO 2
9i
04/24/91
GW
PA IN
SE
8- 12
NORIH
CHEMICO
1226
13 11
92
04/24/91
GIn
•?A I N
SE
B 12
NQRIH
CHEMICO
1 236
1324
9 J
04/24/9 1
GW
«A IN
St
8- 12
NDR1H
C'.Hf M I CO
1 246
13 3 4
04/:>4/9 1
GW
RAIN
S€
8- 12
NORTH
CHEMICO
1 140
1403
9 b
04/2 4/fl 1
GW
QA IN
SF
10- 1 5
NORTH
CHEMICO
1 20U
14 17
96
04/54/91
GW
sain
SE
10 1 5
NORTH
CHEMICO
1 228
1426
97
04/24/91
GW
rain
SE
10- 1b
NOR I H
CHtMICO
1 23fi
1434
98
04/?4/9l
GW
RA IN
SF
10- 1 5
NORTH
CHEMICO
1 248
1445
99
04/35/91
GW
CLEAR
SE
5 10
NORTH
CHEMICO
1206
1238
too
04/25/91
GW
Cl FAR
SF
5 - 10
NOR 1 H
CHtMICO
12 16
1301
101
01/25/9 ^
GW
CLEAR
SE
5 10
NORTH
CHFMICO
1226
1309
102
04/25/9 1
GW
CI FAR
SF
b- 10
NORTH
CHEMICO
1236
1317
litKY 10:48 Tuesday. March 31. 1992
CORPORA I ION
EMISSIONS
EMISSIONS
TOTAL
MAXIMUM
MAXIMUM
DURING
DURING
tMISSlON
OPACJi V
OPACIT
PUSH
TRAVEL
T IMF
DURING
DURING
SECONDS
SECONDS
SECONDS
PUSH. %
TRAVEL,
85
45
130
100
to
70
55
125
100
25
65
45
1 10
85
io
60
40
100
35
5
70
95
165
100
40
65
60
125
30
5
45
45
90
25
0
70
15
1 15
too
30
70
40
1 10
100
30
65
65
130
45
5
75
40
1 15
too
20
70
70
140
75
30
78
60
138
55
lb
45
55
100
65
25
57
55
1 12
B5
15
80
68
148
25
IO
15
0
15
15
0
10
0
10
20
0
7 3
1 5
88
15
5
51
0
51
30
O
36
1H
54
45
10
44
0
44
55
o
61
0
61
50
o
13
0
19
20
O
13
0
13
10
O
20
0
20
15
0
18
0
18
5
O
23
0
23
15
0
56
35
91
65
45
8 1
18
99
35
15
0
0
0
0
O
26
33
59
40
25
50
3 1
81
75
60
54
03
1 17
95
55
69
37
10b
85
30
87
28
1 15
55
15
12 1
4G
167
15
5
62
38
100
15
25
7 i
G2
133
100
20
66
34
100
65
10
62
4 1
103
75
10
75
32
107
70
15
57
28
85
65
10
32
29
61
10
5
27
0
71
25
0
63
34
107
55
10
50
27
05
75
10
66
15
81
90
5
54
29
83
75
15
72
34
106
100
25
81
87
168
100
45
-------
19<
I ME
cr
IN<
XL
4b
35
O
S5
40
10
5
0
45
2 b
tb
20
25
35
25
25
35
40
30
4<)
15
25
30
5
10
40
15
10
15
5
20
O
10
10
25
30
25
45
55
10
25
30
35
20
3b
15
10
40
15
30
35
PUSHING EMISSIONS CONTROL DATA 1!/l? HAT U K*
KI DC DFMONSTRAT ION PROvjFCT - fib THl FHF .V STFFl CORPORATION
SPARROWS POINT. MARYLAND
10:4H Tuesday, March
EMISSIONS
FM1SSI0NS
TOT Al
MAX r MlII
EMI SSIONi
DURING
OURTNG
EMISSION
OPAC IT'
>SLRVtRS
WIND
WIND
OBSERVER
CONTROL
OVlN
time or
PUSH
TRAVEL
r i me
DURING
JIT1ALS
WEATHER
DIRECTION
SPEFO
1OCATION
SYSTEM
POSHFD
PUSH
SFOONDS
SECONDS
SECONDS
PUSH, '
GW
CLEAR
SE
5 10
NORTh
CHEMICO
1246
13 3 1
59
57
1 16
70
GW
CLCAR
SE
5 10
NORTH
CHEMICC
1 148
14 15
48
52
1GO
8b
GW
CLEAR
SL
b 10
NOR I H
CHLMICQ
1208
1432
22
O
22
15
GW
Ct EAR
SE
5- 10
NORTH
CHFMICn
1 23R
1447
48
54
102
90
GW
CLEAR
SE
5- 10
NORTH
CHtMICO
1248
1500
53
49
t02
95
cw
OVERCAST
NE
5 10
NORTH
SHENANGO
1256
i jyy
'J2
2 /
by
30
GW
OVERCAST
NF
5- 10
NORTH
SHENANGO
1 148
1327
43
34
77
65
GW
OVERCAST
NE
5-10
NORTH
SHENANGO
1208
1344
40
32
72
25
GW
overcast
NF
5- 10
NORTH
SHENANGO
i 23fi
1 350
Gft
3 1
09
90
GW
OVERCAST
NE
5-10
NORTH
SHENANGO
1548
1400
52
30
68
60
GW
OVLHCAS1
NL
b 10
NORTH
SHENANGO
1 258
1-112
42
29
7 1
70
gw
OVERCAST
NE
5 10
NORTH
SHENANGO
12CG
1421
54
19
7 J
40
GW
OVERCAST
NE
5 10
NORTH
SHENANGO
1 101
1103
63
67
i y<>
6h
GW
OVERCAST
NE
5-10
NORTH
SHENANGO
113 1
1b 10
4 t
53
94
90
GW
OVERCAST
NE
5- 10
NORTH
SHENANGO
115 1
15 IS
55
66
12 1
55
r.w
CLEAR
SE
4-9
NORTH
SHENANGO
1 126
1250
57
61
118
85
GW
clear
SE
4 9
NORTH
SHENANGO
1206
1316
7 1
4 7
1 18
90
GW
CLLAR
SE
4-9
NOR I H
SHENANGO
1216
1 332
74
38
112
70
GW
CI FAR
SF
4-9
NORTH
SHFNANGO
i?26
1340
66
36
102
85
GW
CLEAR
SE
4 9
NORTH
SHENANGO
1236
134 7
-•8
4 1
99
90
GW
CLEAR
SE
4-9
NORTH
SHENANGO
1246
140b
72
28
100
95
GW
CI FAR
SF
4-9
NOR 1 H
SHENANGO
1 2b6
142 1
22
2 1
53
45
GW
CLEAR
SE
4-0
NORTH
SHENANGO
1 148
1505
4G
39
05
40
GW
CLEAR
SE
1-9
NORTH
SHENANGO
1208
1525
19
34
53
20
GW
CLEAR
SE
4-9
NORTH
SHENANGO
1238
1532
7 2
30
110
7 b
GW
OVEHCAbi
SW
b - 10
NOR 1 H
CMEMICO
1 102
1 14b
73
82
155
fiO
GW
OVERCAST
SW
5- 10
NORTH
CHEMICO
1 152
1200
48
74
1 12
55
GW
OVERCAST
SW
5- 10
NORTH
CMEMICO
1 172
12 15
39
76
135
lOO
GW
OVERCAST
SW
5- 10
NORTH
CHEMICO
1 ??a
1227
5R
46
104
35
GW
OVERCAST
SW
5- 10
NORTH
CHEMICO
1212
1250
45
23
68
20
GW
OVERCAST
SW
5- JO
NORTH
CHEMICO
1222
1312
b2
48
lOO
25
r.w
OVERCAST
SW
5 10
NORTH
CHEMICO
1 232
1319
4 1
0
4 1
2 b
GW
OVERCAST
SW
5 10
NORTH
CHEMICO
1242
1 332
4 4
26
70
30
GW
OVERCAST
SW
b- 10
NORTH
CHEMICO
1262
1 34 3
61
32
93
55
GW
OVERCAST
SW
5 - 10
NORTH
CHEMICO
1 27 2
1 3H9
72
1A
91
90
GW
CI E AR
SW
10- 15
NORTH
SHFNANGO
1 15?
1 137
75
54
120
55
GW
CI E AW
SW
1Q 1 b
NORT 1
SHENANGO
1 172
1 150
C8
5 7
125
7 S
GW
CLEAR
sw
10 15
NORTH
SHENANGO
1212
1200
57
46
103
9 b
GW
CLcAR
SW
10- lb
NORTH
SHENANGO
- 222
1 2 2 -I
66
37
103
ftO
GW
CLEAR
SW
10 lb
NORTH
SHENANGO
',232
1235
72
4 2
1 14
6b
Gw
CI FAW
SW
10- 1b
NOR 1 H
SHENANGO
1242
1 252
65
35
100
60
C M
CLEAR
Sw
10 15
NORTH
SHENANGO
1 202
1302
61
23
84
lOO
GW
CLEAR
SW
10- 15
NORTH
SHFNANGO
1272
1310
73
47
120
100
G W
CI FAR
SW
10- 15
NORTH
SHENANGO
1 134
1323
b8
76
134
100
cw
CI EAR
Sw
10- 15
NORTH
SHENANGO
1 154
1330
7 1
68
139
8 b
GW
CLEAR
SE
3-6
NORTH
SHENANGO
1 167
1 1 IB
58
47
105
85
GW
CLEAR
SE
3-6
NORTH
SHENANGO
1267
1 128
65
22
87
100
GW
CI EAR
SE
3-6
NOR TH
SHFNANGO
1 209
1 143
76
28
104
100
GW
CLEAR
SE
3 6
NORTH
SHENANGO
1229
1 158
36
41
77
90
GW
CLLAR
SL
3 6
NORTH
SHENANGO
1239
1209
7 1
32
103
lOO
GW
CLEAR
SE
3 6
NORTH
SHENANGO
1249
1220
62
29
1 1 1
100
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PUSHING EMISSIONS C'GNIKOL DAfA tt/1'J KATItKV 10:48 Tuesday. March 31, 1992
KIOC DEMONSIKAI ION PROJECT - REfHLtHtM S1FH CORPORATION
SPARROWS POINT. MARYLAND
CM 1 lj j 1 UNS
t MlbSiUNS
1 UT AL
MAXIMUM
MAXIMU
EMISSION
DUPING
during
LMISSI0N
UPA'Ji I Y
OPACi1
OBSERVERS
WIND
Wl
Ni)
HKNFRVf-R
CONTROL
OVEN
TIME OF
PUSH
TRAVEL
TIME
OURING
DURING
OliS
PAf t
INI1IALS
WCAfHCR
DIRECT ION
SPEED
LOCATION
SYSTEM
PUSmFD
PUSH
StCdNOS
seconds
SECONDS
PUSH, %
TRAVEL,
205
0b/30/91
GW
CLEAR
SE
3-
6
NORTH
SHENANGO
1 13b
1 127
4'J2
63
5 1b
100
45
206
O5/30/91
GW
CI EAR
SE
3
G
NORTH
SHENANGO
1 14 J
67
4b
1 12
100
25
?07
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CI FAR
c,c
3-
6
NORTH
SHENANGO
1200
7 1
33
107
KX>
bb
20a
06/04/91
GW
CLEAR
NE
9-
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NORTH
SI If NANC.n
1 135
1 14 1
70
67
137
100
85
209
06/04/91
cw
CI FAR
NF
9-
15
NORTH
SHENANGO
1 153
1207
59
64
123
100
35
2 10
06/04/9 1
GW
CLEAR
NE
9
15
NORTH
SHENANGO
1223
1244
56
28
84
20
20
2 I
06/04/91
r.u
CLCAR
Nt
9
1 5
NORTH
SHLNANGU
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11*54
b 1
2b
86
ICO
45
2 12
06/04/91
GW
clear
NE
9
15
NORTH
SHFNANGQ
12bJ
i:k>7
4 9
27
76
DO
15
213
06/04/9 1
GW
CLEAR
NE
9
15
NORTH
SHENANGO
120b
1323
57?
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b96
100
15
2 14
06/04/91
nw
Clear
NE
«J
15
NORTH
SHLNANGO
12 15
13-16
4 b
39
84
1C0
30
2 15
06/04/91
GW
CLEAR
NE
9-
15
NORTH
SHFNANGO
1225
1359
56
37
93
75
20
2 16
06/04/91
GW
CLLAK
NE
9-
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NOR 1 H
SHFNANGO
1235
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80
65
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2 1?
06/1)4/9 1
GW
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9-
1 b
NORTH
SHENANGO
1245
14 20
52
28
80
6b
1b
2 18
06/ 10/91
GW
NW
b-
10
NORTH
SHFNANGO
1 102
1 124
43 1
56
487
40
10
2 IS
Uo/ 10/91
GW
NW
5-
10
NORTH
SHFNANGO
1 135
1 1h 1
54
67
12 1
100
ioo
22C
06/ 10/91
C»W
NW
5-
10
NOR 1 H
SHFNANGO
1 153
1202
57
G 1
1 18
to
5
22 J
06/ 10/91
oW
NW
5-
10
NORTH
SHFNANGO
120b
12 18
4 9
63
112
10
5
222
06/ lO/D1
GW
NW
5-
10
NOR TH
SHFNANGO
1223
1243
4b
52
98
70
15
223
06/ 10/91
GW
NW
5-
10
NORTH
SHENANGO
1233
IS 58
6b
39
10b
30
10
22 1
06/ 10/91
GW
NW
5-
10
NORTH
SHENANGO
1243
1305
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62
120
3b
30
2 25
06/ 10/91
:;w
NW
5
10
NORTH
SHENANGO
126 J
13 14
7 3
2 1
94
65
15
226
06/ 10/91
GW
NW
b-
10
NORTH
SHENANCO
1215
1330
64
3 b
99
75
15
227
06/ 10/91
GW
NW
5-
10
NORTH
SHFNANGO
1225
1338
A J
4 1
84
100
30
228
06/ 13/91
GW
clear
NW
C
1 7
NORTH
SHENANGO
12/1
1 1 JO
58
? 1
69
100
100
229
06/13/91
GW
CLEAR
NW
6-
12
NORTH
SHENANGO
1 135
1 150
63
69
132
2b
b
230
06/ ! J/91
GW
CLEAR
NW
6-
12
NORIH
SHENANGO
f 153
f 156
74
30
154
7 b
30
2J 1
06/ 1 J/91
GW
CLEAR
NW
6-
1 2
NORTH
SHENANCO
i? in
12 13
78
31
109
db
3b
232
06/13/91
GW
CLEAR
NW
6-
12
NORTH
SHFNANGO
1?23
1245
59
42
101
45
45
233
06/ 1 J/9 1
GW
CLEAR
NW
6-
12
NORTH
SHENANGO
1233
1254
72
34
106
80
80
23 4
06/13/9 1
GW
CLEAR
NW
6-
12
NORTH
SHFNANGO
1243
1304
63
30
93
10
b
235
06/13/91
GW
CLEAR
NW
6-
12
NORTH
SHFNANGO
1263
1312
284
25
309
100
15
236
06/13/91
GW
CLEAR
NW
6-
1 ?
NORTH
SHENANGO
1273
132 1
50
2 7
ab
7 b
10
237
06/ 13/91
GW
CI FAR
NW
6-
1 2
NORTH
SHENANGO
1225
1346
288
32
320
100
0
238
06/ 17/91
GW
CLEAR
NL
6
12
NORTH
SHFNANGO
1268
1 132
77
26
103
100
4 5
239
06/ 17/91
GW
Ct EAR
NE
6
1 2
NOR TH
SHENANGO
1 1 35
1 IhO
H6
49
13b
65
50
240
06/17/91
GW
CLEAR
Nfc
6-
2
NORTH
SHENANGO
1 102
1200
1f>1
23
174
bO
b
24 1
Ob/ 1 //91
GW
CLEAR
Nr
6-
5 2
NORTH
SHENANGO
1 153
1224
64
42
10b
bo
20
2 12
06/ 17/9\
Gw
CI FAR
N1
6-
1 ?
NORTH
SHENANGO
1201
1233
A3
33
H2
30
10
213
06/ 17/91
GW
CI FAR
NF
6-
12
NORTH
SHENANGO
12 11
124C
72
13
1 15
ah
30
244
06/ 17/91
Gw
C l i AR
Nf
6-
• 2
NOW 1 H
SHENANGO
122 1
1 2bb
78
4 1
1 19
Hb
hO
245
06/ 17/91
Gw
CI CAR
Nf
6-
i **
NOR TH
SHINANGO
i?3 i
1 303
46
37
83
15
25
246
06/ 17/91
GW
CLEAR
NF
6-
12
NORIH
SHENANGO
124 1
132b
7 b
3b
1 10
40
30
24 7
06/ W/31
GW
CM FAR
Nl-
6-
1 2
N03TH
SHFNANGO
1251
I 346
uu
J 1
1 t9
fOO
40
2 18
06/ 18/9 t
GW
OVFRCAST
Sr
5-
*0
NORTH
SHENANGO
2 b 0
1 120
69
28
97
65
25
219
06/ 18/91
GW
OVFROAST
SF
b-
10
NOR TH
SHENANGO
1260
1 1J8
64
34
98
7 b
45
250
06/ 18/91
CW
OVf-RCA Sf
Sfr
5-
10
NORTH
SHENANGO
J2L»5
120!
65
23
88
60
251
06/18/91
GW
OVFRCAST
SE
b-
10
NOW 1 H
SHENANGO
1 13b
1222
53
56
109
80
80
252
OS/ 18/91
GW
OVERCAST
S£
b
•o
NORIH
SHENANGO
1 1b3
1240
58
62
120
10
10
253
06/ IB/9 1
GW
0VERCAS1
SL
i> -
:o
NORTH
SHENANGO
1201
I25S
63
69
132
6b
20
204
06/18/9 1
GW
OVERCAST
SE
b-
10
NO KITH
SHFNANGO
12 11
1330
59
44
103
8b
1b
255
06/18/91
GW
OVERCAST
SE
5-
10
NORTH
SHFNANGO
12? 1
1340
CG
48
1 14
8b
10
-------
19!
I Ml
tCI'
>IN<
'El.
15
30
1<)
15
20
25
5
5
15
5
3'j
30
15
3S
15
20
50
1b
2.5
5
20
25
10
60
30
15
20
5
15
5
35
20
20
10
65
BO
BO
10
10
10
15
4b
25
oo
20
15
2b
1b
10
5
70
DUSKING EMISSIONS CONTROl 0A1 A 1 1/ 12 HAIII-KY 10:46 Tuesday. March
KI DC DEMONSTRATION PROJECT - BETHLEHEM STEEL CORPORATION
SPARROWS POINT. MARYLAND
EMISSIONS
EMISSIONS
10 T AL
MAX 1 Ml
EMISSION
DURING
DURING
EMISSIUN
OPACI
3SERVERS
WIND
WIND
OBSERVER
CONTROL
OVEN
TIME OF
PUSH
IRAVEl
I IMF
OUR I N<
MI TIALS
WEATHER
DIRECTION
SPEED
LOCATION
SYSTEM
PUSHED
PUSH
SECONDS
SECONDS
SECONDS
PUSH,
G W
OVERCAST
SE
5
0
NORTH
SHENANGO
123 1
1400
6 1
45
106
75
GW
OVERCAST
SE
[i-
0
NQHIH
SHtNANGU
124 1
112 1
58
33
91
60
GW
CLEAR
SWSNW
5-
0
NORTH
CHFMICO
1111
1 1 19
6ft
76
1 4 1
30
GW
CI FAR
SW&NW
5-
0
NORTH
CHEMICO
1 135
1 132
57
72
129
10O
gw
CLEAR
SWSNW
5
0
NORTH
ChEMICD
1 153
1 140
63
68
13 1
15
GW
CLEAR
SW&NW
b
o
NORTH
CHEMICO
1226
1201
68
61
129
75
GW
CLEAR
SW&NW
b-
c
NORTH
CHEMICO
1246
1241
52
37
89
35
GW
CLLAR
SW&NW
5
0
NOR HI
CHEMICO
1208
1258
56
49
105
30
GW
CLEAR
SW&NW
5-
o
NORTH
CHEMICO
1248
13 11
61
46
107
80
GW
CLEAR
SW&NW
5-
0
NORTH
CHEMICO
I2b8
1322
73
44
1 17
10
Gw
CI FAR
SW&NU
5 -
o
NORTH
OhFMICO
12G8
1328
46
4 9
9b
6 b
GW
CLEAR
SWSNW
5
0
NORTH
CHEMICO
1101
1347
54
73
127
75
GW
SL
B
2
NOR I'M
CHEMICO
123d
1250
4 1
38
78
75
GW
SE
e-
2
NORTH
CHEMICO
1248
1300
68
3H
107
55
GW
SF
R-
2
NOR 1H
CHFMICO
1255
13 1 fl
42
38
80
25
Gw
SE
6-
2
NORTH
CHEMICO
1258
1330
54
4 3
97
60
C.W
SF
B
2
NORTH
CHEMICO
1268
1342
73
3?
1 10
80
GW
SE
8
2
NORTH
CHEMICO
1 101
1355 '
57
62
1 iy
bO
GW
SE
o
2
NOR III
CHEMICO
1 1G4
14 10
G 1
53
1 14
100
GW
SE
8-
2
NORTH
CHEMICO
1201
1428
70
63
133
70
GW
SE
B
2
NORTH
CHEMICO
12 11
1436
76
48
124
90
GW
SE
fi-
2
NORTH
CHFMICO
12? 1
14 4b
7 1
43
1 14
75
GW
OVFRCAST
NF
9-
5
NORTH
SHENANGO
1 151
1 120
54
49
103
55
GW
OVERCAST
NF
9-
5
NORTH
SHENANGO
1 13b
1 132
6 2
by
121
85
GW
OVERCAST
NE
9-
5
NOR IH
SHENANGO
1 lb J
1 144
55
51
106
70
GW
OVERCAST
NE
9-
5
NORTH
SHENANGO
I 126
1 157
43
56
99
45
GW
OVERCASI
Nt
9-
5
NORTH
SHENANGO
I23G
12 18
51
48
03
40
GW
OVERCAST
NF
9
5
NORTH
SHENANGO
1246
1224
46
32
78
1b
GW
OVERCAST
NF
9-
5
NORTH
SHENANGO
1208
1240
50
47
97
20
GW
OVERCAST
Nt
9-
5
NORTH
SHENANGO
1228
1302
58
35
93
4b
GW
OVERCAS!
Nt
9-
b
NORTH
SHFNANGO
1238
13 12
47
41
03
75
GW
OVERCASI
NE
9-
5
NORTH
SHENANGO
1248
1319
44
38
82
80
GW
OVERCAST
SE
6-
2
NORTH
SHENANGO
1231
1440
68
41
109
85
GW
OVERCASI
SF
6-
2
NORTH
SHENANGO
124 1
1502
77
32
109
70
GW
OVERCAST
SE
6-
2
NORTH
SHENANGO
1251
1510
64
43
107
7 b
GW
OVERCAST
SE
6-
2
NORTH
SHENANGO
126 1
15 17
8 1
37
1 1H
HO
GW
GVFRCASI
St
6-
n
NORTH
SHFNANGO
127 1
1524
73
33
10C
80
GW
OVERCAST
SF
6-
2
NflRTH
SHENANGO
1 125
1552
78
73
1 b 1
7 b
GW
OVERCAST
SL
6
2
NORTH
SHENANGO
1 1 54
1 b 1 2
6b
69
135
60
GW
OVERCAST
sc
G
2
NORTH
SHENANGO
1 167
162 1
6 1
67
12H
35
GW
OVERCAST
SE
6
2
NURIH
SHLNANGU
12 13
1636
72
44
1 16
85
GW
OVERCAST
SE
6-
2
NORTH
SHENANGO
1223
1G4?
68
4 1
109
100
GW
CI FAR
NW
6-
2
NORTH
SHENANGO
1151
1 1 16
63
70
133
4b
GW
C. FAR
NW
6-
2
NORTH
SHENANGO
1 135
1 131
9 1
6b
1b6
100
GW
clear
NW
6
2
NORTH
SHENANGO
1 153
1 MO
82
61
143
55
GW
CLEAR
NW
6
2
NORTH
SHENANGO
1226
1 156
162
33
195
100
GW
CLEAN
NW
6
2
NORTH
SHENANGO
12 36
1 2 lO
57
36
1 13
40
GW
CLEAR
NW
6-
2
NORTH
SHFNANGO
1246
1 223
76
39
115
100
(iW
CLEAR
NW
6-
2
NORTH
SHENANGO
1255
1239
52
31
83
45
GW
Ct FAR
NW
6-
2
NORTH
SHENANGO
1208
1254
47
33
BO
2b
GW
CLEAR
NW
6
2
NORTH
SHENANGO
1238
1303
88
37
125
100
-------
19!
;iMt
kCI"
!IN<
'EL
100
4 b
5
30
50
20
10
35
100
25
10
25
70
10
5
b
2b
3'J
40
45
60
15
'JO
50
35
15
bb
40
55
55
i CO
00
1b
15
IO
15
30
35
25
40
20
20
15
25
20
45
35
30
2b
PUSHING CM1SSIONO CONTROL DMA 11/12 dATTLRY
K1DC DEMONSTRATION PROJECT - BLTHLEHEM STEEL CORPORATION
SPARROWS POINT. MARYLAND
10 4B Tuesday,
March
lMISSION
JBSbRVtWS
WIND
WIND
ORSERVFR
CONTROL
OVfKl
TIMF OF
INI I LAIS
WFAfHFR
DIRECTION
SPEED
LOCATION
SYSTEM
PUSHED
PUSH
GW
CI tAR
NW
6-12
NORTH
SHENANGO
1248
131 1
GW
ClLAk
NW
b- 10
NUKIH
SHtNANGO
1 13b
1 137
GW
Ct EAR
NW
5- 10
NORTH
SHFNANGO
1 153
1 14G
GW
Ci FAR
NW
5-10
NORTH
SHENANGO
1226
121 1
GW
CI EAR
NW
5- 10
NORTH
SHENANGO
1 236
1216
GW
clear
NW
5 10
NORTH
SHENANGO
124G
1255
GW
CLEAR
NW
5- 10
NORTH
SHENANGO
12 DB
1314
GW
CLEAR
NW
5 10
NORTH
SHENANGO
1228
1328
GW
CLEAR
NW
5- 10
NORTH
SHENANGO
1239
1344
GW
CLEAR
NW
5 10
NORTH
SHENANGO
1240
1352
GW
CLEAR
NW
5 10
NORTH
SHENANGO
1250
I^O'J
GW
CLEAR
NES-SE
5- 10
NORTH
SHENANGO
1232
1 1 b3
GW
CLLAR
NL&St
b- 10
NUKfH
SHENANGO
1 lb 1
12 13
GW
CI EAR
Nk&St
5-10
N0R1H
SHENANGO
1 S 35
123 1
GW
CLEAR
NL&SE
5- 10
NORTH
SHLNANGO
f 103
12.18
GW
CLEAR
NLSSE
5- 10
NORTH
SHENANGO
1 1 £8
1247
GW
Ct EAR
NE&SE
5- 10
NORTH
SHENANGO
124 2
1304
GW
CI FAR
NF8SF
5- 10
NORTH
SHFNANGO
1262
1312
GW
Ci EAR
NC&SF
h - 10
NOR 1H
SHFNANGO
1 ? i?
\:v?i
GW
CI FAR
NF5SE
5- 10
NORTH
SHENANGO
12 14
1345
GW
CLEAR
NE&SE
5-10
NORTH
SHENANGO
1224
1353
GW
CLEAR
SE&SW
4 3
NORTH
CHLMiCO
1 1b1
1 1 2'J
GW
CLfcAR
SESSW
4 9
NORTH
CHEMICO
1 135
1 145
GW
CLEAR
SE&SW
4-9
NORIH
CHEMICO
1 153
1 156
GW
CLEAR
SE&SW
4-9
NORTH
CHEMICO
1222
1228
GW
CI FAR
SFRSW
4-9
NORTH
CHFMICO
12G2
1316
GW
CLEAR
SE&SW
4-9
NORTH
CHEMICO
1272
1 32b
GW
Ct EAR
stssw
4 9
NORTH
CHEMICO
1242
1400
GW
CI FAR
SfcSStf
4-9
NORTH
CHEMICO
1214
1406
(iW
CI EAR
SFftSW
4-9
NORTH
CHfcMICU
1224
1423
GW
CLEAR
SE&SW
4 9
NORTH
CHEMICO
1234
143 1
GW
SE
5 10
NORTH
SHENANGO
1 148
1124
GW
SC
5 10
NOR IH
SHENANGO
! 1 b 1
1 1 b2
GW
SE
5-10
NORTH
SHENANGO
1 135
1 TM 6
GW
Sfc
5- 10
NORTH
SHENANGO
1 153
123 1
GW
sf
5- 10
NORTH
SHFNANGO
1222
1243
r.w
sf-
5 - 10
NORTH
s ienango
1222
1301
GW
SE
5- 10
NOKIH
SHLNANGO
1242
13 '6
GW
•>t
¦i H>
NOR IH
SHt NANC.O
1 ?»-.?
1 n ? •;
GW
SE
5-10
NORTH
SHENANGO
u> rj
133b
uw
bL
'j JO
NORIH
SHENANGO
12 M
134b
Gw
OC .PAIN
S*
4 m
NORTH
SHENANGO
1 1 r.'A
1 lb 7
GW
OC.RAlN
Sw
4 10
NORTH
K I DC
1151
1232
GW
CC ,RA1N
5 w
4 10
NORTH
S 1ENANGU
1229
124b
GW
OC .RAIN
SW
4 10
NORTH
SHENANGO
1242
i?b6
GW
UC .RAIN
SW
4-10
NORTH
SHENANGO
1262
1303
GW
CC.RAIN
sw
4- !0
NORTH
SHENANGO
1272
13*5
GW
nr.pain
sw
4 10
NORTH
SHENANGO
1 135
1335
GW
QC.RAIN
Sw
4- 10
NORTH
SHENANGO
1160
1348
Gw
OC.RAIN
S*
4 - 10
NORIH
SHENANGO
12 14
1402
GW
UC.RAIN
sw
4- 10
NORTH
SHENANGO
1224
1409
•MISSIONS
EMISSIONS
TOTAL
MAXIMUI
DURING
DURING
EMISSION
OPAC I 1'
PUSH
TRAVEL
TIMF
DURING
SECONDS
SECONDS
SECONDS
PUSH, '
81
32
1 13
100
68
69
137
100
59
64
143
50
209
40
249
too
76
46
122
100
57
38
9b
100
*>K
4 1
ion
40
6 1
42
103
45
bB
46
104
100
7 b
39
1 14
IOO
67
3 b
10?
hb
59
31
90
50
57
62
1 19
80
64
88
152
100
hfi
.91
14 7
6b
bO
fib
13b
lb
55
34
89
20
52
29
81
100
54
30
84
90
62
36
88
95
80
66
92
1 5?
6b
56
95
ifcrt
100
62
87
149
40
65
47
1 12
55
62
38
10O
100
65
31
SG
90
b /
ua
9b
3 b
59
43
102
10U
b2
4G
3d
6b
6b
bO
1 15
100
fc1
67
128
100
52
63
l 15
100
57
7A
136
100
48
66
1 14
25
6 ^
3 1
feb
4 b
46
33
79
40
57
30
87
60
Si
27
fi 1
100
62
26
68
100
45J
42
SI
80
6 1
B3
144
50
10
63
44
107
55
57
40
97
70
66
3ft
94
45
61
35
96
60
71
68
139
8b
b9
66
125
90
74
42
1 16
30
65
40
105
80
-------
PUSHING EMISSIONS CUN1RUL UAIA 11/12 BAilLRY
KIDC DCMON.STRAT IDN PROJFCT - RFTHIFHFM STFFl CORPORATION
SPARROWS POINT. MARVI AND
1048 Tuesday, March
31, 1992
S
I MISSIONS
LMISSIONS
TOTAL
MAXIMUM
MAX I Ml
EMISSION
DURING
DURING
EMISSION
OPACI!Y
OPACI"
OBSERVERS
WIND
WIND
OBSERVER
CONTROL
OVEN
TIME OF
PUSH
TRAVEL
T IMF
DURING
mm inc
ass
DATE
INITIALS
WEATHER
DIRECTIUN
SPEED
LOCA I ION
SYS 1 EM
PUSHED
PUSH
SFCONDS
SFCONDS
SFCONDS
PUSH. %
TRAVEL
358
07/29/H1
RF A
RAIN
NF
m
NORTH
SHENANGO
1 1 b S
1 146
107
105
212
95
50
359
07/29/9!
SfiP
RAIN
NE
5- 10
NORTH
SHENANGO
1 151
1 146
107
105
2 12
80
4 b
~ GO
07/20/D 1
GW
OC .RAIN
NE
5- 10
NORTH
SHENANGO
115 1
1 14b
10b
107
2 12
75
45
3bt
07/29/91
REA
RAIN
NE
10
NORTH
SHENANGO
1 135
1 157
60
90
1 bO
100
65
362
07/29/91
SBP
RAIN
Nfc
b- tO
NORTH
SHtNANGU
1 135
1 157
65
85
150
100
60
363
07/29/9 1
GW
OC .RAIN
NE
5- 10
NORTH
SHFNANf.n
1 1 3*
1 15ft
f.7
88
155
100
6 b
364
07/29/91
REA
RAIN
NE
10
NORTH
SHENANGO
1 153
1224
59
35
94
50
35
365
07/23/9 1
SBP
RAIN
NE
5 10
NORTH
SHENANGO
1 153
1224
60
30
9()
bO
30
366
07/29/9 1
GW
OC.RAIN
NE
5- 10
NORTH
SHFNANGO
1 153
1 225
7 1
48
1 19
bb
30
367
07/?9/3 1
RF A
RAIN
NF
10
NORTH
SHENANGO
1222
1244
103
52
155
35
100
368
07/29/3 1
SBP
RAIN
NF
5- 10
NORTH
SHFNANGO
1222
1 24*1
103
52
155
85
100
369
07/29/91
GW
OC.RAIN
MG
5 tO
NORTH
SHENANGO
1222
1244
89
52
1 4 1
80
10O
370
07/20/9 1
Re a
RAIN
NE
10
NORTH
SHENANGO
1232
1256
4 1
0
4 1
35
0
J 7 1
07 / 29/ -2 1
SB^
Rain
•NE
5 10
NORTH
SHENANGO
12 3 2
12b6
>11
o
4 1
30
0
'YD
07/29/3 I
GW
OC.RAIN
NE
b to
NOR I H
SHENANGO
1232
1257
43
o
43
30
r>
J/J
0//29/9•
GW
OC.RAIN
NE
b- 10
NOR 1 H
SHENANGO
1 101
1422
h ft
68
124
80
40
) / 4
07/?<4/9 1
GW
or,RAIN
NI-
5- 10
NOR 11 i
SHENANGO
1 224
14 36
BG
42
126
90
45
J ! b
OV/29/91
GW
OC.RAIN
NE
5 10
NORTH
SHFNANGO
1234
1 444
82
48
130
100
100
370
07/29/9 1
GW
OC,RAIN
NE
b 10
NORM
SHENANGO
1244
1454
76
A'J
1 19
40
15
377
07/29/9 1
aw
OC.RAIN
NL
5 10
NORTH
SHENANGO
I ? 16
1509
59
40
99
45
10
378
07/30/91
GW
OVERCAST
SE
5- 10
NORM
CHEMICO
1151
1 139
58
66
124
65
10
379
07/30/31
GW
OVERCAST
SE
S 10
NORTH
CHEMICO
1 135
1 146
63
72
135
100
7 O
380
07/30/91
GW
OVERCAST
SE
5 10
NORTH
CHEMICO
1 153
1202
44
69
113
40
25
3B1
07/30/9t
GW
OVERCAST
SE
5 10
NORTH
CHEMICO
1218
1221
0
o
0
O
0
382
07/30/9 1
GW
OVERCAST
5C
5 10
NORTH
CHEMICO
1232
1255
67
4b
1 12
2 b
f>
383
07/30/9 1
GW
OVERCAST
SE
5 10
NORTH
CHFMICO
i?4?
1325
70
40
1 10
15
5
384
07/30/91
GW
OVERCAST
Sfc
5-10
NORM
CHEMICO
1222
1340
68
53
121
100
30
385
07/30/91
GW
OVERCAST
SE
5 10
NORTH
CHEMICO
1262
1357
78
33
1 1 1
90
35
386
OV/30/91
GW
OVERCAST
SE
5- 10
NORTH
CHEMICO
127?
140*
57
31
88
75
20
387
07/30/9 1
GW
overcast
SF
5- 10
NORTH
CHEMICO
1214
1423
4G
52
D8
35
45
388
08/01/91
GW
Clear
SE/SW
5 10
NORTH
KIDC.
1 148
1 1 15
89
89
30
2 b
3Q9
08/0*/9 1
GW
clear
SE/SW
5 10
NORM
SHENANGO
1135
1125
56
7 1
127
100
too
390
oe/01/91
aw
clear
SE/SW
5-10
NOR 1 H
KIDC
1 lb 1
1 143
1 16
34
150
bb
40
391
08/01/9 1
GW
CLEAN
SE/SW
5- 10
NORTH
SHENANGO
1222
1 158
7 1
73
144
G5
GO
392
08/01/91
GW
CLEAR
SE/SW
5- 10
NORTH
SHFNANGO
1 153
1207
49
68
1 17
55
30
393
08/0V91
GW
clear
Nuf
7 12
NORM
SHENANGO
1 148
112a
84
72
156
100
30
3 9'J
08/05/91
GW
Clear
NW
7 - 12
NORTH
SHENANGO
1 1 b 1
1210
7 7
85
16?
35
20
395
08/05/91
GW
Cl t ak
NW
I- 12
NORTH
SHtNANGU
1 135
1232
82
86
168
100
100
396
OB/Cj/9 1
GW
clear
NW
7 12
NORTH
SHFNANGO
1 153
1240
7H
76
1 Sh
30
1 b
397
Ofi/Cn/9 1
GW
Cl FAR
N W
7-1?
NOR 1 H
SHENANGO
12 17
1301
8 1
54
135
7 b
35
396
06/05/9 1
GW
Clear
Nw
7- 12
NORTH
SHENANGO
1229
1310
68
38
106
2 b
10
399
OR/05/9 1
GW
Ct_E AR
Nw
7 12
NORM
SHENANGO
1237
1325
75
b 1
126
100
45
400
OB/05/9 1
GW
Cl.E ar
NW
7 12
NORT H
SI If"NANGO
124 7
1 34 1
HO
3 b
t 1b
1O0
25
401
OB/Ob/91
GW
Clear
NW
7 12
NORM
SHLNANGO
1 149
1403
59
82
14 1
100
45
402
08/C5/9I
GW
C L fc A R
NW
7- 12
NORTH
SHtNANGU
11*09
1 420
7 4
48
122
25
10
403
OB/Oo/9 1
GW
Cl EAR
SE
5 10
NORTH
SHFNANGO
1 144
1 132
61
89
150
100
100
404
08/06/9 1
GW
clear
SF
5-10
NORTH
K I 00
1 151
1152
126
50
176
20
5
405
0B/C6/9 1
GW
clear
SE
5 tO
NORTI1
SHENANGO
1217
12 15
74
98
172
90
50
406
OC/CG/9 1
GW
clear
SE
5- 10
NOR T H
SHENANGO
11b3
1226
42
65
1 17
50
20
40/
O8/06/3 1
aw
clear
SE
b- 10
NORTH
SHLNANGU
1237
1 2bB
66
5 1
1 17
85
45
408
08/C6/9 1
GW
Cl EAR
SE
5- to
NORTH
SHFNANGO
1 304
63
62
12b
100
60
-------
PUSHING EMISSIONS CQNTROI DA IA 1 1 /12 BATTERY 10 4B Tuesday, March
KI DC DEMONSTRATION PROULCT - BETHLEHE.M bfEEt CORPORATION
SPARROWS POINT. MARYLAND
31, 1992
tMISSIONS
cMISSIONS
TOTAl
MAXIMUM
MAX TMUF
EMISSION
DURING
DURING
EMISSION
OPACITY
opacity
C1RSFRVFRS
WIND
WIND
G-JSERVER
CONTROL
OVcN
l1Mb OF
PUSH
IKAVtL
I IMF
DURING
DURING
HKS
DATE
initials
WEATHER
DIRECTION
SPEED
LOCATION
SYSTEM
PUSHED
PUSH
SECONDS
SECONDS
SECONDS
PUSH. %
TRAVEI ,
40^>
OB/o^/91
:;w
CI 1 AR
SL
5 - 10
NORTH
SHENANGO
1 2 17
in 14
57
40
97
t>b
410
08/06/91
GW
CLEAR
SL
5- 10
NORTH
SHFNANGO
1257
1324
S1
0
51
15
O
4 1
08/0G/91
GW
CLEAR
bt
b 10
NUN J H
SHENANGO
1209
1349
47
25
72
25
10
412
08/OG/91
GW
CLEAR
SE
h- 10
NORTH
SHENANGO
1239
1357
54
4 2
96
7 b
15
413
08/12/91
GW
CLCAR
SE
b- 1b
NHH !H
SHFNANGO
1 135
1 <26
226
81
307
100
75
4 14
08/12/9 1
GW
CLEAR
SE
5 15
NOR 1 H
SHFNANGO
1 1 5 1
1 149
85
86
17 1
100
70
4 lb
08/12/9 1
GW
CI EAR
SE
5 - 15
NOR 1 H
SHENANGO
120 1
1203
€0
7 1
139
100
25
4 16
08/12/91
GW
CI EAR
SF
5 15
NORTH
SHENANGO
1 153
1222
83
7 b
VjS
40
20
4 7
OB/ 13/91
GW
OVERCAST
SF
4 rt
NOR FM
K I L>C
1 1 40
1 130
8 3
3 f 9
462
20
O
4 ia
08/ 1 :i/5} 1
r,u
OVERCAST
SE
4 8
north
CHEMICO
1 1 35
1 lb 1
89
95
184
lOf)
60
•1 13
08/13/91
GW
OVERCAST
Sf.
4-8
NORTH
KI DC
MS 1
1201
6 1
627
688
30
30
420
08/13/91
GW
OVERCAST
S l
4 -R
NORTH
CHEMICO
1248
12 19
fc'J
j 1
140
70
20
421
08/13/91
GW
OVERCAST
SF
4-8
NORTH
CHEMICO
1 1 33
1229
72
57
129
50
10
4 22
Cd/ 13/9 1
GW
OVERCAST
Sf
4 -a
NORTH
CHEMICO
1267
123B
64
JG
100
bb
2b
42 3
0-3/13/9 1
GW
C.i t AH
se
4-8
NORTH
CHEMICO
125R
1 3(J0
78
36
t 14
9S
4G
a 2-1
08/13/91
GW
CLtAR
St
4-B
NORTH
CHEMICO
12GS
1330
82
39
12 1
70
45
42b
08/13/9!
GW
CLEAR
Sl
4 -8
NORTH
CHEMICO
1238
1345
87
49
136
85
75
4 ?fc>
OB / IV 9 1
Gto
CLEAR
s z.
4 8
NOR f H
CHEMICO
1 20 1
140^
209
4G
2bb
HO
lO
•12 7
03/14/91
GW
OVERCAST
Ss
b- 10
NORTH
SHENANGO
12C8
1306
74
50
124
50
25
428
08/ 14/01
GW
UVERCAoI
SL
b- 10
NOW IH
SHENANGO
1243
132 1
72
40
1 12
30
25
•123
03/ 14/91
GW
OVERCAST
SF
5- 10
NORTH
SHENANGO
1258
1335
69
42
1 1 1
4b
3b
4 30
08/14/91
GW
OVERCAST
SE
h- 10
NURIH
SHtNANtiO
126ft
1352
66
36
102
50
30
43'
08/ 14/91
(iW
OVERCAST
SE
5 10
NORT H
SHENANGO
1201
14 15
77
49
12G
05
'2 b
432
08/14/91
GW
UVERCAS1
SE
5- 10
NORTH
SHENANGO
12 11
1424
n 1
30
433
08/19/91
GW
OVERCAST
NW
lO- 1b
NORTH
CHfcMICO
1 135
1 1 19
€9
34
103
45
2C
4 34
08/ 1fl/fl1
GW
overcast
NW
10 1b
NURIM
CKtMlCU
12 17
1 127
73
73
30
10
4 35
08/ 19/91
GW
OVERCAST
NW
10 15
NORTH
CHEMICO
1 148
1 138
44
68
1 12
100
35
4 36
08/19/91
GW
OVERCAST
NW
10 15
NOR J11
CHLM1CU
1 1b1
1209
b3
73
126
85
70
43?
08/19/91
GW
OVERCAST
NW
10 15
NORTH
CHEMICO
1 1l»3
1227
48
5
63
20
5
438
08/19/91
GW
UVERCAST
NW
10-
NORTH
CHEMICO
123b
1244
65
50
115
00
65
439
08/19/91
GW
OVERCAST
NW
10 b
NORTH
CHfcMICO
1246
1251
53
18
7 1
85
1C
440
08/19/91
GW
QVCRCAS1
NW
10- 1b
NORTH
CHEMICO
1208
1301
69
0
10
0
441
08/19/91
GW
OVERCAST
NW
10- 1b
NOR IH
CHfcMICO
1238
1314
58
33
91
100
35
44?
OB/19/91
Cw
OVCRCASI
NW
to 1b
NOR 1 H
CHEMICO
1248
1323
6 1
42
107
100
40
443
08/20/y1
GW
OVERCAST
NW
10- 15
NORTH
CHFMICO
1 148
1223
56
65
12 1
90
lb
444
08/20/9 1
GW
CVFRCAbI
NW
10- 1b
NOR 1 H
CHFMICO
1 151
1244
63
68
131
75
50
•14 0
08/2U/y1
GW
CVERCAS1
NW
10- 15
NORTH
CHrMICO
1 •. 3 b
I2b<)
b 2
94
140
100
8 b
•1 16
08/20/91
GW
DVENCAS 1
NW
10- 1 h
NORTH
CHFMICO
1 153
1302
50
38
88
75
10
44 i
08/20/9 1
Gw
CVfRCASf
NW
10 'n
NORTH
CHEMICO
1 -2G
1313
66
94
162
20
10
4 18
08/20/9?
C>w
r.Vl RCAS I
NW
10 in
NOB fM
CHEMICO
1 2 3G
1329
a 7
4 4
14 1
85
25
449
08/20/91
GW
overcast
NW
10 1b
NORTH
CHEMICO
i 24G
1340
61
4 1
102
35
10
¦4 50
08/20/9!
GW
OVERCAST
NW
10 1b
NORTH
CHLMICO
1208
I3bb
40
0
40
30
0
-15 1
03/20/0 1
CW
CVFRfAST
NW
10 15
NORTH
CHfcMICO
12 38
14 11
7 1
33
109
fi5
AO
452
08/20/91
GW
OVERCAST
NW
10 15
NOR I H
CHEMICO
1248
1423
69
34
103
90
25
453
08/2G/91
GW
LLCAR
0 10
NOR 1 H
SHhNANGO
1 148
1 1 19
J 19
64
183
75
25
454
08/26/9 1
GW
CLEAR
SE
5- 10
NORTH
SHFNANGU
1 13b
1 140
89
Get
157
too
100
455
08/2G/91
GW
CLEAR
SE
0- 10
NORTH
SHENANGO
1 151
1147
74
62
136
100
100
4bG
08/2G/91
GW
CLEAR
SL
b- 10
NOR 1 H
SHENANGO
1 153
1157
h€>
65
12 1
GO
4 b
457
08/26/91
GW
CLtAR
SE
5- 10
NORTH
SHFNANGO
1236
1238
7fi
40
116
100
40
4bB
08/26/S1
GW
CI t-AK
SE
5- 10
NORTH
SHENANGO
1246
1247
62
35
97
1O0
20
4b9
08/26/91
GW
CI FAR
SE
S 10
NORTH
SHENANGO
1208
1304
b8
43
101
50
25
-------
19<
I Ml
.CI
!IN<
'EL
45
30
35
35
15
35
10
35
45
55
45
55
35
25
45
15
35
65
20
55
40
45
lO
60
20
2C>
40
0
30
40
45
35
30
40
3b
45
10
10
3D
SO
25
75
100
35
35
30
40
100
30
60
PUSHING fcMlSSiriNS CONTROi OA T A 11/1/ RATTERY 10:48 Tuesday. Marcn
Kmc; OFWONSTRATION PWOJfCI - eETHLEHFM SfbfcL CORPORA!ION
SPARROWS POINT, MANY! AND
LMI jjiUNS tMlSSIONS total maximum
CMI SSI ON
DURING
DURING
EMISSION
OPACi1
OBSERVERS
WIND
WIND
UbSLKVER
CONTROL
OVLN
UML OF
PUSH
TRAVEL
TIME
DURINC
INI r IAI s
WE ATHl R
l>i Kfc C 1 luN
SPEfcU
IOCAT KIN
SYSItM
PUSHfcU
PUSH
si <;un»s
SECONDS
SECONDS
PUSH.
GW
CLLAR
S L
5 10
NORTH
SHENANGO
1238
1333
99
37
136
ioo
GW
CLEAR
Sfc
b- 10
NOR 1 H
SHfcNANCO
124fl
1340
7 1
35
106
too
GW
CLEAR
SE
5- 10
NORTH
SHLNANGG
1258
1354
66
40
106
55
GW
OVERCAST
SE
5 10
NORTH
CHEMICO
1 153
1 16?
66
60
1?fc
90
GW
(JVtRCAS1
SE
5- 10
NORTH
CHFMICO
1226
1203
54
42
96
85
uw
OVERCAST
St
b- 10
NURIH
CHtMICO
1236
1215
61
68
129
70
GW
OVERCAST
SF
0- 10
NOR 1 H
CHFMICO
12 16
1227
39
44
83
75
GW
OVFRCAST
SF
5- 10
NORTH
CHFMICO
1208
1234
67
4 1
108
1C0
GW
OVERCAST
SF
5- 10
NORTH
CHFMTCO
1228
124 1
46
49
95
100
GW
OVERCAST
SE
5 lO
NORTH
CHEMICO
1236
1252
53
47
ioc>
100
GW
OVERCAST
sr
5- 10
NORTH
cnrMico
1248
1300
52
40
92
85
GW
OVFRCAST
SE
5- 10
NORTH
CHEMICO
1258
1309
47
36
83
85
r.w
OVFRCAST
SE
5- 10
NORTH
CHEMICO
1 2C8
13 3 1
55
SO
105
80
GW
OVERCAST
SOUTH
10-20
NORTH
SHENANGO
123 1
1449
GO
4 1
107
65
GW
OVERCAST
SOUTH
10-20
NORTH
SHENANGO
124 i
14 50
72
44
1 16
9 b
(,W
OVERCAST
SOUTH
10-20
NORTH
SHENANGO
12b 1
1509
59
47
106
75
GW
OVLKCASI
SOUTH
10-20
N0R1H
SHENANGO
1 2 b 7
1b 16
62
40
102
30
GW
OVERCASI
SOU 1 H
10-20
NORTH
SHENANGO
126 1
1525
78
36
1 14
ICO
GW
OVERCAST
SOUTH
10-20
nor T H
SHENANGO
127 1
1533
83
29
1 12
ICO
GW
UVLRCAST
SOUTH
10-20
NORTH
SHENANGO
1 13-1
1615
53
74
132
35
GW
OVERCAST
SOUTH
10- 20
NORTH
SHENANGO
1 15-1
1630
65
ft 1
146
80
GW
OVERCAST
SOU TH
10 20
NORTH
SHFNANGO
12 13
1640
71
42
1 13
75
GW
OVERCAST
SOUTH
10-20
NORTH
SHENANGO
1223
1650
63
46
109
85
GW
Cl TAR
NE/NW
10 15
NORTH
KI DC
t 118
1 125
23
3 1
54
20
GW
CLEAR
NE/NW
10-15
NORTH
CHEMICO
1135
1 139
86
78
164
100
GW
CLEAR
NE/NW
10-15
NORTH
KI DC
1151
1 152
28
49
7 7
10
GW
01 FAR
NE/NW
10 15
NORTH
CHEMICO
123G
1203
95
86
181
9 b
GW
CLEAR
NE/NW
10 lb
NORTH
CHEMICO
I1b3
12 14
62
43
105
100
GW
CLEAR
NF/NW
10 lb
NORTH
CHEMICO
1246
12 36
b2
0
52
10
(iW
CLEAR
Nt/NW
10- lb
NORTH
CHtMICO
1208
1242
77
46
123
55
GW
CLEAR
NE/NW
10 15
NORTH
CHEMICO
1238
i:>b 1
bb
48
103
90
GW
CLEAR
NL/NW
10 15
NORTH
CHEMIC3
1248
1300
66
4 b
1 1 1
60
GW
CLEAR
NE/NW
10- 15
NORTH
CHLMICf}
1258
1309
57
38
9b
80
GW
CLEAR
SL/SW
b 10
NORTH
CHtMrca
1 148
1 129
73
6 1
134
ICO
GW
CLEAR
SE/SW
5 10
NORTH
CHEMICO
i 135
1 153
8?
73
155
100
CW
CI FAR
SE/SW
5 10
NORTH
CHEMIC3
1151
1203
57
cr>
123
bb
GW
Cl EAR
SF/SW
5- 10
NOR 1H
CHFMICO
12 36
12 10
75
34
1 12
100
GW
Cl FAR
SF/SW
5-1 Ci
NORTH
CHFMTCn
1 1 K3
1 ? 4 1
01
74
t 37
30
GW
CL FAR
SF/SW
5- 10
NOR I H
CH-MIC"!
1246
1253
50
38
97
60
GW
Ci TAR
St/SW
b- 10
NOR IH
CHtMICJ
1208
13 1b
6 1
52
! 13
40
f;w
CL EAR
SE/SW
5 lO
NORTH
CHEMICa
r.'im
i:) 2 b
7'.a
42
1 1 7
100
GW
CLEAR
sr/sw
5 10
NORTH
CHrMI CO
(248
13J4
68
13
f ! 7
70
GW
CLEAR
SE/SW
5 lO
NORTH
CHEMICU
I2S8
13bl>
/o
3 b
10b
7 b
GW
OVERCAST
sw
1b 20
NORTH
SHENANGO
113b
1 138
63
65
1 28
ICO
GW
OVERCAST
sw
1b 20
NORTH
SHENANGO
1236
1 MB
60
53
1 13
70
GW
OVERCAST
sw
15 20
NORTH
SHENANGO
1246
122 1
66
3 1
99
6b
GW
OVERCASI
sw
lb-20
NORTH
SHENANGO
1 153
1232
72
50
122
55
GW
OVEHCAST
sw
15-20
NOR IH
SHENANGO
1208
124b
81
39
120
ICO
GW
OVERCAST
sw
Ib-VO
NUR IH
SHENANGO
1238
1308
56
43
99
75
GW
UVERCAS1
S*'
lb-20
NORTH
SHENANGO
1248
132 1
6 1
37
Ofl
75
GW
UVLRCAS1
sw
15-20
NOR 1 H
SHENANGO
1258
1329
53
47
100
90
-------
PUSHING FMISS1QNS CONTROL DA 1A tt/12 BAIIERV 10.4B Tuesday. March 31. 1992 11
KIDC DEMONSTRATION PROJECT BETHLEHEM STCCL CORPORATION
SPARROWS POINT. MARYIAND
EMI'jUlONS
EMISSIONS
fOTAl
MAXIMUM
MA X i MUt
EMISSION
DURING
DURING
EMISSION
OPACITY
OPACIT'
OBSERVERS
WIND
WIND
OBSERVER
CONTROL
OVEN
time of
PUSH
TRAVEL
TIM}-
DUHi NG
OURING
obs
DATE
INITIALS
WLATHLtf
DIRECT ION
SHLfcO
LOCAliON
5Y5TEM
PUSHFO
PUSH
St-CONDS
SECONDS
SECONDS
PUSH. %
TRAVEL,
51 1
09/ 17/91
GW
CLEAR
SW/NW
6 1 2
NORTH
SHENANGO
1 148
1 12 1
7 8
62
140
100
80
5 12
09/17/9 1
GW
CLEAR
SW/NW
€-12
NORTH
SHfcNANGO
1 135
1 144
67
65
132
100
7h
513
09/17/91
GW
CLEAR
SW/NW
6-12
NORTH
SHFNANGO
1151
1 154
74
70
144
100
55
5 14
09/17/9 1
GW
clear
SW/NW
6-12
NORTH
SHENANGO
1200
12 lb
KO
43
IG3
100
65
5 15
09/17/91
GW
CLEAR
SW/NW
6-12
NORTH
SHFNANGO
1 150
1228
73
66
130
75
45
51G
09/17/91
GW
CLLAR
SW/NW
6-12
NOR IH
SHFNANGO
1206
1245
68
39
107
100
50
5 1 7
09/17/91
GW
CI t AR
SW/NW
6-12
NOR IH
SHENANGO
1208
1255
66
49
1 15
85
45
5 18
09/ 17/91
GW
CLEAR
SW/NW
6 12
NORTH
SHFNANGO
123fi
1303
77
45
122
100
100
519
09/17/91
GW
CLEAR
SW/NW
6 - 12
N0R1H
SHENANGO
1248
13 13
ft?
37
1 19
100
65
520
09/ 17/91
GW
CLEAR
SW/NW
6 12
NORTH
SHENANGO
125U
1324
7 1
40
t 1 1
ICO
40
52 1
09/ 18/91
GW
OVERCAST
SE
G-12
NOR IH
SHENANGO
1258
13 13
67
44
1 1 1
too
100
522
09/18/91
GW
OVERCAST
SE
fc-12
NOR IH
SHFNANGO
126R
132 1
83
31
1 14
100
100
09/ lb/9 1
GW
UVEWCAS i
SF
6 12
NORTH
SHENANGO
1201
1329
62
4G
too
55
30
524
09/ in/9 1
GW
OVfcRCAST
St
6 12
NOR 1 H
SHENANGO
12 11
1338
55
48
103
SO
40
525
09/18/91
GW
OVERCAST
SL
to- 12
NOR ! H
SHfcNANGU
122 f
134 7
58
54
112
ion
65
526
0CV 1ft/9 1
GW
OVERCAST
SL
6 12
NORTH
SHENANGO
123 1
1356
67
37
104
fiO
*5
5 2 7
09/ IU/bl
GW
OVERCAST
SE
6 12
NORTH
SHFNANGO
124 1
1404
7fl
43
1? 1
100
40
5 28
09/16/01
GW
OVERCAST
S E
6 12
NOR iH
SHFNANGO
1 2'j 1
11 16
63
4 1
1C4
100
100
'j29
09/18/9 1
GW
OVfcHCAS?
SF
6- J?
NOR IH
SHENANGO
1255
14 33
58
35
93
4 5
35
y:JO
09/ 10/91
GW
uveRCASi
St
6-12
NOR ! H
SHENANGO
126 1
1448
65
42
107
70
40
5 3 1
ow/^y/y1
GW
UVERCAS i
sw
15-20
NORTH
SHENANGO
1 113
1 120
58
72
130
75
60
hJ2
09/23/91
GW
UVEKCASi
sw
15-20
NORTH
SHFNANGO
1 135
1 129
B 1
78
159
100
100
533
09/2 3/91
GW
OVERCAST
sw
15-20
NORTH
SHFNANGO
115 1
1 13R
83
7 1
154
65
35
534
09/23/91
GW
OVhRCAST
sw
15-20
NORTH
SHFNANGO
1 216
1 161
7G
40
122
75
5l>
535
09/23/91
GW
OVERCAST
sw
15-20
NORTH
5HENANGO
1 153
1200
65
67
132
50
20
536
09/23/91
GW
OVERCAST
sw
15-20
NORTH
SHFNANGO
1 240
12 1 1
89
42
131
100
60
537
09/23/91
GW
OVERCAST
sw
15 20
NORTH
SI IF NANGO
117 1
1223
91
62
153
30
25
538
03/23/91
GW
OVERCAST
sw
15-20
NORTH
SHENANGO
1200
1236
85
46
123
75
45
h39
09/23/91
GW
overcast
sw
15-20
NORTH
SHENANGO
1233
124G
97
47
154
65
30
540
09/23/91
GW
OVERCAST
r»w
15 20
NORTH
SHENANGO
12-18
1259
83
39
12?
20
15
541
09/24/91
GW
clear
EAST
10 15
NORTH
SHFNANGO
1151
1 144
83
65
148
95
65
54 2
09/24/H1
GW
GLt AW
1 AS I
10- 15
NORTH
SHENANGO
I23S
1 ID9
78
47
125
100
35
54 3
09/24/91
GW
CLEAR
EAST
10- 15
NORTH
SHFNANGO
1 153
12 12
ft A
69
157
45
25
544
09/24/91
GW
CI FAR
EAST
10-15
NORTH
SHENANGO
1246
1229
97
36
133
1b
15
545
09/24/91
GW
CLf-AR
FAS \
10-15
NORTH
SHENANGO
1 171
1238
1 IG
85
201
100
100
546
C3/24/H1
GW
CLCAR
LAST
10 15
NORTH
SI IE NANGO
1203
1251
/ 4
63
137
55
30
547
09/24/91
GW
CLEAR
EAST
10 15
NCRTil
SHENANGO
1229
1305
95
43
148
10
5
543
00/25/9 t
GW
CLOY
NW
ii - H)
NOR i H
SHfcNANGO
11/1
1333
63
59
127
100
75
549
09/25/91
GW
CLUV
NW
5-10
NORTH
SHENANGO
i?oa
1352
72
54
126
85
40
550
09/25/91
GW
CI DY
NW
5- 10
NOR I H
SHFNANGO
1238
1400
61
38
99
100
1C0
551
10/01/91
GW
Cl FAR
Sw
fi - i 2
NORTH
VHLNANGO
1222
1 130
57
34
9 1
1b
10
55?
10/01/91
GW
C. 1 FAR
SW
6-12
NORTH
SHENANGO
1 135
1202
88
66
154
100
1C0
553
10/02/91
GW
Cl FAR
SW
5-10
NORTH
CHEMICO
1200
1432
31
10
A 1
10
5
554
10/02/91
GW
CLEAR
Sw
5 10
NCR IH
CHEMl CO
17 29
1452
b1
33
87
40
20
555
10/04/91
REA
CLEAR
s
5
NORTH
SHENANGO
1 135
12 U)
121
101
22 1
100
75
h5G
10/O4/S1
Kt A
CLEAR
s
5
NOR I i 1
SHENANGO
1 153
12 18
1 13
57
170
80
55
557
10/0-1/91
REA
CI FAR
5
5
NORTH
SHENANGO
1244
1236
130
33
133
60
20
508
10/04/91
REA
CLEAR
s
5
NORTH
SHENANGO
1216
1250
105
49
154
100
80
559
10/04/91
Rt A
Cl FAR
s
5
NORTH
SHENANGO
122G
13 10
103
4 7
150
65
50
560
10/04/91
REA
CLEAR
S
5
NORTH
SHENANGO
1236
1321
61
101
162
90
80
561
10/08/91
GW
CLEAR
NW
6-12
NOR H i
SHENANGO
1 t 34
1 1 16
737
54
791
100
15
-------
PUSHING EMISSIONS CCNTRCl DATA 11/1? BATTFRY
KIDC DEMONSTRATION PRO.iFCT - EfcTHl EHFM STEFi CORPORAUON
SPARROWS POINT. MARYIANO
10-4A Tunuday, Morc>"> 31, 1092 12
EMISSIONS
EMISSIONS
TOTAt
MA X MUM
MAXIMUI
tM[SSI ON
DURING
DURING
EMISSION
OPACIrv
OPACIT
OBSERVERS
WIND
WIND
OBSERVER
CONTROL
OVEN
timf in
HUSH
7RAVFI
I IMF
DURING
DURING
OBS
DA! b
INITIALS
WLAIHLR
DIRECTION
SPLLU
LOCATION
SYSTEM
PUSHED
PUSH
SECONDS
SECONDS
SECONDS
PUSH, /.
TRAVEL.
562
10/08/91
r.w
CLEAR
NW
6- 12
NORTH
SHFNANGO
1224
1 159
86
45
131
70
30
563
10/08/9 t
GW
CLEAR
NW
6 12
NORTH
5HLNANG0
1 234
1203
t»6
4 1
107
75
15
564
10/08/91
G W
CLEAR
NW
G 12
NORTH
SHENANGO
1244
12 17
7 3
4 8
12 1
75
10
565
10/08/91
GW
CLEAR
NW
6 12
NORTH
5HENANG0
1216
1234
82
50
132
90
55
566
10/09/91
GW
CLEAR
SE
5- 10
north
SHkNANGO
1 134
1 132
B4
68
152
R5
25
567
10/09/91
GW
CLLAM
Sfc
b- 10
north
SHENANGO
1224
1 157
56
52
108
65
20
56fi
10/09/91
GW
CLEAR
SE
5- 10
NORTH
SHkNANGO
1234
12 11
/a
6 1
139
90
40
bbW
10/O9/91
GW
CL t AR
SE
5- 10
NORTH
SnENANGO
1244
I 225
58
43
101
45
20
570
10/09/91
GW
CLEAR
SE
fa- 10
NORTH
SHFNANGO
1? 1G
1244
62
50
112
50
25
57 1
10/11/91
GW
CLEAR
SE
10- 15
NORTH
SHFNANGO
1224
1 144
63
51
1 14
65
55
572
10/ 1-1/9 1
GW
CLEAR
SE
10-15
NORTH
SHKNANGn
1 ?:i4
1 ? 7
B4
4*
129
100
40
573
10/14/91
GW
CLEAR
SF
10- 15
NORTH
SHENANGO
1256
1703
48
35
83
Tb
10
574
10/14/91
GW
CLEAR
SE
10 15
NORTH
SHENANGO
126 1
1 rja
86
4 3
129
75
15
575
<0/15/01
GW
OVERCAST
C E
5 12
NORTH
SI ILNANGU
1 134
11 - 10
NORTH
SHFNANGO
1 134
1 136
65
15
80
85
10
585
10/23/91
GW
OVERCAST
SF
5- 10
NORTH
SHENANGO
1224
1 155
/ 1
38
109
75
25
586
10/23/91
GW
OVFRCAST
SE
5- 10
NORTH
SHENANGO
1234
12 Ob
54
45
99
100
35
587
10/23/91
GW
OVERCAST
SE
5 10
NORTH
SHENANGO
1258
1442
7 7
35
1 12
50
15
586
10/23/91
GW
OVERCAST
SE
5 10
NORTH
SHENANGO
1 *68
14«; y
58
4 1
99
35
10
580
10/24/91
CW
HAZY/OC
SF
5 10
NORTl1
SHENANGO
1234
1 144
6b
4 1
106
45
15
590
10/24/91
GW
HAZY/OC
SF
b 10
NORTH
SHENANGO
1258
1442
54
4 3
97
100
30
591
10/28/9 1
GW
CLEAR
NE
8-1?
NORTH
SHENANGO
13 28
1443
35
10
4 5
30
5
592
J0/28/91
GW
CLEAR
NE
8-12
NORTH
SHFNANGO
1 238
1 45V
5 7
36
93
100
25
593
10/28/91
GW
Cl EAR
NE
6- 12
NORTH
SHENANGO
1248
1500
55
25
80
100
10
504
10/28/91
GW
C. FAR
NE
R 12
NORTl 1
SI ILNANGU
125b
1 b 1
6 1
38
99
40
40
505
to/?ft/m
GW
CI FAR
ME
R 12
NORTH
SHENANGO
11CQ
1526
58
27
8 b
100
20
596
10/29/91
GW
CI FAR
NF
ft- 12
NORTH
SHENANGO
1228
1443
35
10
4 5
30
5
597
10/29/9 \
GW
C. FAR
NE
R- \?
NORTH
SHENANGO
1236
1452
57
93
lOO
25
598
10/29/91
GW
Ci FAR
NF
8 1?
north
SHENANGO
1 2 4 H
moo
3 5
25
80
100
10
599
10/29/9 1
r.w
(• ar
Nt
8- 1?
NORIH
SHENANGO
1250
15 ' t
G 1
36
99
40
40
GOO
10/29/9l
r.w
r. *• ar
NF
ft - 1 2
NORT 1 1
SHTNANGO
12C b
1'jJO
bB
2 7
85
100
20
6o 1
'0/30/H1
l.W
Cl F AR
NW
6- 1?
NOR 1 H
SHENANGO
1258
lb 09
57
36
93
75
35
CO 2
;C>/ 30/9 1
GW
Ci Ear
NW
6-12
NOR 1 H
SHFNANGO
1 268
iS'b
7 |
42
1 13
80
40
603
10/30/9 1
r.w
r.t ear
MIn
r, - 12
NORTH
SHI NANGf.
1 r- 01
1 S '.i 1
H 4
7 3
157
100
35
604
10/30/9 1
GW
Ci FAR
NW
6- 12
north
SHENANGO
121 1
1540
8a
.17
136
30
30
605
10/JO/9 1
GW
Ci fc AR
NW
6- ?
north
SvfNANCO
122 1
1540
GU
58
126
30
30
606
1 1/05/9 1
GW
CI FAR
NF
6 12
NORTl 1
SHENANGO
1234
1 152
4 20
4 3
163
80
20
607
11/05/91
GW
CL FAR
NE
6- 12
north
SHENANGO
1268
1408
64
33
97
100
25
608
11/05/91
GW
Cl EAR
Nf
b- ?
NORTH
SHtNANGO
1 20 1
1517
bO
57
107
70
10
609
1 1/05/y 1
GW
Cl EAR
NF
6- 12
NORTH
SHENANGO
12 11
1524
67
52
1 19
65
50
G 10
51/05/9 1
GW
CLEAR
NE
6- 12
NORIH
SHtNANGO
122 1
1531
61
55
1 16
85
30
6 1 1
'1/Ob/91
GW
CLLAR
Nfc
b- 2
NOR 1 H
SHFNANGO
123 1
1538
72
42
1 14
100
45
612
11/06/91
GW
C. EAR
SE
6- 12
NOR f H
SHtNANGO
1224
1 123
240
4 I
281
90
10
-------
PUSHING EMISSIONS CONTROL DATA 11/12 BATTFRY
KIDC DEMONSTRATION PKOJfcCI - RHHiFHFM SfEEL CORPORA T I ON
SPARROWS POINT, MARYLAND
10 4ft Tuesday. March 31. 1992 13
EMISSIONS
EMISSIONS
IOI AL
MAXIMUM
MAX IMUI
lMISSION
OJRTNG
DURING
FMISSION
OPACITY
OPAC IT
OBSfRWFRS
WIND
WIND
OBSERVER
C0NTR01
OVEN
TIME OF
PUSH
TRAVEL
TIMC
OURING
DURING
DBS
UAIt
INITIALS
weather
DIRECTION
SPEED
LOCATION
SYSTEM
PUSHED
PUSH
SECONDS
SECONDS
SECONDS
PUSH. %
TRAVEL,
6 13
1 l/Cft/9i
GW
€! FAR
St
6- 12
NORTH
SHFNANGO
1201
1 b2b
63
44
107
100
30
6 14
1 t /C6/9 1
GW
Ci FAR
St
6- 12
NORTH
SHFNANGO
12 11
1b
b9
37
9G
20
10
615
1 1/07/91
GW
OVERCAST
SE
4 ft
NORTH
SHFNANGO
12 16
1 250
94
43
137
10O
30
6 16
1 1/07/9 1
GW
UVtKCAST
SF
4-8
NORTH
SHENANGO
1226
1267
8 1
4 1
122
eo
10O
fc 17
11/12/91
REA
OVFRCAST
NIF
5- U>
WEST
SHFNANGO
1 224
1 128
9b
6/
162
60
35
6 18
11/12/91
Rt A
OVERCAST
NE
5 10
WEST
SHENANGO
1244
1 14 1
60
40
100
50
2b
C 19
11/12/91
RCA
OVERCAST
NE
5- 10
WEST
SHtNANGU
12 10
1 150
45
37
82
3b
25
620
1 1/12/91
KLA
OVLRCASt
NL
IO
WEST
SHENANGO
1226
1202
6t»
•11
106
BD
CO
62 1
11/12/91
REA
OVERCAST
NE
b- IO
WFS!
SHENANGO
1236
122 1
56
30
86
65
40
b 22
1 1/13/9 1
REA
WES I
5- 10
NORTH
SHENANUU
1 KM
1 128
4()
47
87
50
15
623
1 1/13/9 1
RF A
WFST
5- IO
NOR 1 H
SHFNANGO
1224
1 142
152
20
172
15
5
624
11/13/91
REA
WEST
5 10
NORTH
SHENANGO
1244
1 152
1 16
30
146
60
25
625
1 1/13/9 1
REA
WEST
r 10
NORTH
SHENANGO
12 10
120G
108
60
168
30
10
626
1 1/13/9 1
RCA
WCST
5- 10
NORTH
SHENANGO
1226
1224
b6
3-1
SO
6 b
15
627
4 1/21/91
GW
SHENANGU
1236
1234
72
34
106
7 b
as
6 2B
* 1/21/21
GW
SHENANGO
1 2'16
12-16
6-1
28
92
100
25
629
• 1/21 /9 1
GW
SHFNANGO
1238
14 53
72
48
120
100
60
fcJO
*. 1/21/91
GW
SHFNANGO
1248
1502
131
53
134
100
50
t;:) i
i i / 2 1 / 9 1
GW
SHENANGO
1258
15 12
76
42
i ia
100
A\>
fe'J2
1 1/22/9 1
GW
OVERCASI
SE
IO- lb
NOR IN
SHENANGO
1224
1 1 bO
1 12
4 1
1S3
100
30
63 3
1 1/22/9 1
GW
OVERCASI
Sfc
IO tb
NORTH
SHENANGO
1234
120O
292
44
3.16
100
35
foJ-3
< 1 /22/S1
GW
OVERCAST
SE
10- 15
NORTH
SHFNANGO
12 34
1232
38
39
77
100
15
63h
• 1/22/9 1
GW
OVERCAST
SE
10 15
NORTH
SHENANGO
1244
1245
91
45
136
100
45
C3C
1 1/22/9 1
GW
OVFRCASI
St
10- IS
NOR 1 H
SHENANGO
1226
1250
74
40
114
75
20
637
1 1/22/91
GW
UVLRCAST
5t
10 15
NORTH
SHENANGO
12 36
13?5
57
•16
103
BO
30
-------
Section 4
Pushing Emissions T-test Comparison of the Conventional Control
Systems vs. the KIDC System
A-3B
-------
PuSHlNO EMISSIONS OPACI1Y I 1EST
K i DC VS All CONVtNllUNAL PUSHES
MAX OPACITY DURING PUSH VS. MAX OPACIFY Rtf-ORE- TGNI1IOK (CQMPV1)
MAX OPACITY CURING T RAVF1 VS MAX OPACITY AfTER IGNIT I ON (CflMPV?)
\?:Q! lliursaay, July 2, 1932
TTFST PR3CEDURF
var ^ fib1 e : COMPV 1
i YFL N
Std Oev
Std Error
V;.ir i trices
Df
ProD>|T|
CONV fcS9
ooooot- *oo
100 C'JOOOOGO
40.OOOOOOOO
OOOO
p-nt>> j 1 I
Unequal
F qua i
18.3290
11 1
d 1« s
339 0
o. ooo 1
o oooo
TIME Of- rMibMONb Tl'jl
KilK: VS. Ail CONVENT I (1NAI PUSHES
TIME QF FMTSSIONS OUR ING PUSH (EDP)
fl^f OF FMISSIONS CURING ^RAVFl (EDI)
1? (W Ihui&Uay. ~u1y 2. 1D92
11ES1 PROCEDURE
Vanaole; LUP
TYPE N
CONV
KitfC
623
232
Mean
7 1 .K0G£d790
7 2.07 758G2 1
For* HO- Variances am equal.
Std Dev
52.1051545£
39. 167b6 1 20
Std Error
2 07927202
2 b7 14 7G37
(, 211 )
Minimum
O.OOOOOC'OO
1 .OOOOOt 4-01
Max1mur
737 OOOOOOOO
4 43.OOOOOOOO
Prob>F '
0 OOOO
Var i ances
IJneq^a I
Equal
0 1424
-O 1252
DF
545 .8
*58 .0
Pncb>|T|
o.asea
0.9004
VanahUr H)1
TVPF N
CONV
K 1 DC
G26 4C.0977C358
242 120.611h702b
Strt r.pv
20 34f>19^B2
83.04013c43
Siti
o.e uiossc
5 33802G0O
Mo v
17 I OOOOOCOC
492 IXXXJOQOO
Vnriances
Unequa1
Equa 1
13 . 0517
-20.6789
25 2
8-afi
|T|
O OOO 1
0 OOOO
for HO: Var •• «jru.:t.'s> Jiro uljuj I , F' 16. oG
or
( 24 1. sr>?s)
Pr-utor • - 0.0000
-------
Appendix B
Visible Emission Observation Data & Suinnary Tables - Pushside, Topside,
and Discharge & Handling Emissions
Table of Contents
Section Page
1 Pushside Emission Observations Conventional vs. KTDC - B-2
Overall & Monthly.
2 Topside Emission Observations Conventional vs. KIDC - B-6
Overall & Monthly.
3 Quenched Coke Discharge & Handling Emissions Conventional B-15
vs. KIDC - Overall & Monthly.
4 Pushside Emission Observations Conventional & KIDC - B-19
Database.
5 Topside Emission Observations Conventional & KIDC - B-39
Database.
6 Quenched Coke Discharge & Handling Emissions - B-b9
Conventional 4 KIDC - Database.
7 Emission Statistic T-test Results. B-96
B-l
-------
Section 1
Pushside Emission Observations Conventional vs. KIDC
Overall & Monthly
-------
PUSHER SIDE OVEN EMISSIONS OBSERVATIONS STATISTICS
CONVENTIONAL PUSHES
OVERALL STATISTICS
MARCH - NOVEMBER, 1991
AVERAGE
VALUE
STANDARD
DEVIATION
MAXIMUM
VALUE
MINIMUM
VALUE
NUMBER OF OBSERVATIONS = 283
CUMULATIVE EMISSION TIKE, SECONDS 57.4 29.6
MAXIMUM OPACITY, % 51.4 32.7
165
ICO
KIDC PUSHES
OVERALL STATISTICS
OCTOBER - NOVEMBER, 1991
AVERAGE
VALUE
STANDARD
DEVIATION
MAXIMUM
VAL'JE
MINIMUM
VALUE
NUMBER OF OBSERVATIONS = 125
CUMULATIVE EMISSION TIME, 5ECONDS 59.0 21.3
MAXIMUM OPACITY, % 61.9 35.9
109
:oo
3
10
B-3
-------
PUSHER SIDE OVEN EMISSIONS OBSERVATIONS STATISTICS
CONVENTIONAL PUSHES
MONTHLY STATISTICS
AVERAGE
VALUE
STANDARD
DEVIATION
MAXIMUM
VALUE
MINIMUM
VALUE
MAR91 4 OF OBS.= 10
CUMULATIVE EMISSION TIME,
MAXIMUM OPACITY, %
SECONDS
84.7
35.5
8.6
L4.2
95
55
65
10
APR91 * OF 0BS.= 49
CUMULATIVE EMISSION TIME,
MAXIMUM OPACITY, %
SECONDS
69.0
50.7
29.0
33.9
135
100
10
5
MAY91 * OF OBS.c 30
CUMULATIVE EMISSION TIME,
MAXIMUM OPACITY, %
SECONDS
55.2
56.2
27.4
33.3
90
ICO
JUN91 4 OF 0BS.= 10
CUMULATIVE EMISSION TIME,
MAXIMUM OPACITY, %
SECONDS
70.5
67.5
39.0
36.8
145
LOO
10
15
JUL91 if OF OBS. = 61
CUMULATIVE EMISSION TIME,
MAXIMUM OPACITY, %
SECONDS
55.6
51.2
30.9
29.9
124
100
10
5
AUG91 if OF OBS. = 43
CUMULATIVE EMISSION TIME,
MAXIMUM OPACITY, h
SECONDS
45.1
51.6
23.1
34.5
113
100
SEP91 # OF OBS.= 39
CUMULATIVE EMISSION TIME, SECONDS 43.8
MAXIMUM OPACITY, % 44.6
OCT91 # OF OBS.= 26
CUMULATIVE EMISSION TIME, SECONDS 66.7
MAXIMUM OPACITY, % 50.4
20.8
35.5
30.3
29.7
79
LOO
165
100
16
IS
NOV91 # OP OBS.= 15
CUMULATIVE EMISSION TIME,
MAXIMUM OPACITY, %
SECONDS
57.9
63.3
36.7
35.0
127
100
5
15
B-4
-------
PUSHER SIDE OVEN EMISSIONS OBSERVATIONS STATISTICS
KIDC PUSHES
MONTHLY STATISTICS
AVERAGE STANDARD MAXIMUM MINIMUM
VALUE DEVIATION VALUE VALUE
OCT91 4 OF OBS.» 67
CUMULATIVE EMISSION TIME, SECONDS 55.7 18.7 89 16
MAXIMUM OPACITY, % 65.2 33.7 100 10
N0V91 * OF OBS.= 58
CUMULATIVE EMISSION TIME, SECONDS 61.6 23.8 109 5
MAXIMUM OPACITY, % 53.1 38.2 100 10
B-5
-------
Section 2
Topside Emission Observation Conventional vs. KIDC -
Overall & Monthly
B-6
-------
COKE OVEN TOPSIDE EMISSIONS OBSERVATIONS STATISTICS
CONVENTIONAL PUSHES
MONTHLY STATISTICS
AVERAGE
VALUE
STANDARD
DEVIATION
MAXIMUM
VALUE
MINIMUM
VALUE
MAR91 # OF OBS.= 17
CUMULATIVE EMISSION TIME,
MAXIMUM OPACITY, %
SECONDS SO.2 34.7
50.0 31.6
90
100
APR91 # OF OBS.= 34
CUMULATIVE EMISSION TIME,
MAXIMUM OPACITY, %
SECONDS 54.2
43.4
45.0
27.9
210
100
MAY91 ff OF OBS.= 50
CUMULATIVE EMISSION TIME,
MAXIMUM OPACITY, %
SECONDS 56.4 24.4
39.4 30.2
93
100
JUN91 # 0? OBS.= 30
CUMULATIVE EMISSION TIME,
MAXIMUM OPACITY, %
SECONDS 93.5
41.8
79
31
480
100
25
5
JUL91 # OF OBS.= 65
CUMULATIVE EMISSION TIME,
MAXIMUM OPACITY, %
SECONDS 46.0 29.7
44.6 32.4
170
100
AUG91 4 OF OBS.= 37
CUMULATIVE EMISSION TIME,
MAXIMUM OPACITY, %
SECONDS 4C.6
52.6
22.8
34.7
116
100
SEP91 # OF OBS.= 38
CUMULATIVE EMISSION TIME,
MAXIMUM OPACITY, %
SECONDS 40.5 18.9
56.3 40.5
81
100
CCT91 # OF OBS.= 25
CUMULATIVE EMISSION TIME,
MAXIMUM OPACITY, %
SECONDS 49.7 46.2
50.4 34.8
259
100
14
10
NOV91 # OF OBS.= 16
CUMULATIVE EMISSION TIME,
MAXIMUM OPACITY, %
SECONDS 46.9
56.9
57.8
39.4
251
IOC
0
0
B-7
-------
COKE OVEN TOPSIDE EMISSIONS OBSERVATIONS STATISTICS
CONVENTIONAL PUSHES
OVERALL STATISTICS
AVERAGE
VALUE
STANDARD
DEVIATION
MAXIMUM
VALUE
MINIMUM
VALUE
NUMBER OF OBSERVATIONS- 312
CUMULATIVE EMISSION TIME, SECONDS 54.1 51.8
MAXIMUM OPACITY, % 47.1 33.5
5B5
100
KIDC PUSHES
OVERALL STATISTICS
AVERAGE
VALUE
STANDARD
DEVIATION
MAXIMUM
VALUE
MINIMUM
VALUE
NUMBER OF OBSERVATIONS- 97
CUMULATIVE EMISSION TIME, SECONDS 73.0 32.8
MAXIMUM OPACITY, % 80.5 25.4
329
100
38
20
B-8
-------
COKE OVEN TOPSIDE EMISSIONS OBSERVATIONS STATISTI
CONVENTIONAL PUSHES
MONTHLY STATISTICS
AVERAGE STANDARD MAXIMUM
VALUE DEVIATION VALUE
MAR91 # OF OBS.= 17
CUMULATIVE EMISSION TIME, SECONDS 50.2 34.7 90
MAXIMUM OPACITY, °s 50.0 31.6 100
APR9L # OF OBS.= 34
CUMULATIVE EMISSION TIME, SECONDS 54.2 45.0 210
MAXIMUM OPACITY, % 43.4 27.9 ICO
MAY91 # OF OBS.- 50
CUMULATIVE EMISSION TIME, SECONDS 56.4 24.4 55
MAXIMUM OPACITY, % 39.4 30.2 100
JUN91 # OF OBS.= 30
CUMULATIVE EMISSION TIME, SECONDS 93.5 79.2 480
MAXIMUM OPACITY, % 41.8 31.1 100
JUL91 t OF OBS.= 65
CUMULATIVE EMISSION TIME, SECONDS 54.1 73.2 585
MAXIMUM OPACITY, % 44.6 32.4 100
AUG91 # OF OBS.= 37
CUMULATIVE EMISSION TIME, SECONDS 40.6 22.8 116
MAXIMUM OPACITY, % 52.6 34.7 100
SEP91 # OF OBS.= 38
CUMULATIVE EMISSION TIME, SECONDS 10.5 18.9 81
MAXIMUM OPACITY, % 56.8 40.5 100
OCT91 * OF OBS.= 25
CUMULATIVE EMISSION TIKE, SECONDS 49.7 46.2 2S9
MAXIMUM OPACITY, i 50.4 34.8 100
NOV91 # OF OBS.= 16
CUMULATIVE EMISSION TIME, SECONDS 46.9 57.8 251
MAXIMUM OPACITY, % 56.9 39.4 100
B—9
-------
COKE OVEN TOPSIDE EMISSIONS OBSERVATIONS STATISTICS
KIDC PUSHES
MONTHLY STATISTICS
AVERAGE
VALUE
STANDARD
DEVIATION
MAXIMUM
VALUE
MINIMUM
VALUE
OCT9I # OF OBS.= 63
CUMULATIVE EMISSION TIME,
MAXIMUM OPACITY, %
SECONDS
74.6
78.7
39.8
25.9
329
IOC
41
20
NOV91 if OF OBS.= 34
CUMULATIVE EMISSION TIME, SECONDS 70.0 12.1
MAXIMUM OPACITY, % 83.8 24.5
90
100
38
25
B-IO
-------
COKE OVEN TOPSIDE EMISSIONS OBSERVATIONS STATISTICS
CONVENTIONAL. PUSHES
OVERALL STATISTICS
AVERAGE STANDARD MAXIMUM MINIMUM
VALUE DEVIATION VALUE VALUE
NUMBER OP OBSERVATIONS3 312
CUMULATIVE EMISSION TIME, SECONDS 52.4 42.2 480 0
MAXIMUM OPACITY, % 47.1 33.5 100 0
KIDC PUSHES
OVERALL STATISTICS
AVERAGE STANDARD MAXIMUM MINIMUM
VALUE DEVIATION VALUE VALUE
NUMBER OF OBSERVATIONS= 97
CUMULATIVE EMISSION TIME, SECONDS 73.0 32.8 329 38
MAXIMUM OPACITY, % 80.5 25.4 100 20
B-Xl
-------
CDKE OVEN TOPSIDE EMISSIONS OBSERVATIONS STATISTICS
CHEMICO PUSHES
OVERALL STATISTICS
MINIMUM
VALUE
0
0
MINIMUM
VALUE
0
0
B-12
AVERAGE
VALUE
STANDARD
DEVIATION
MAXIMUM
VALUE
NUMBER OF OBSERVATIONS^ 76
CUMULATIVE EMISSION TIME, SECONDS 54.2 36.3
MAXIMUM OPACITY, % 43.6 31.1
210
100
SHENANGO PUSHES
OVERALL STATISTICS
AVERAGE
VALUE
STANDARD
DEVIATION
MAXIMUM
VALUE
NUMBER OF CBSERVATIONS= 236
CUMULATIVE EMISSION TIME, SECONDS 51.3 43.9
MAXIMUM OPACITY, % 46.3 34.2
480
100
-------
COKE OVEN topside: emissions: observations statistics
CONVENTIONAL PUSHES
MONTHLY STATISTICS
AVERAGE STANDARD MAXIMUM MINIMUM
VALUE DEVIATION VALUE VALUE
MAR91 # OF OBS.= 17
CUMULATIVE EMISSION TIME, SECONDS 50.2 34.7 90 1
MAXIMUM OPACITY, % 50.0 31.6 100 5
APR91 # OF 0BS.= 34
CUMULATIVE EMISSION TIME, SECONDS 54.2 45.0 210 2
MAXIMUM OPACITY, % 43.4 27.9 100 5
MAY91 # OF OBS.- 50
CUMULATIVE EMISSION TIME, SECONDS 56.4 24.4 95 0
MAXIMUM OPACITY, % 39.4 30.2 100 0
JUN91 f OF 0BS.= 30
CUMULATIVE EMISSION TIME, SECONDS 93.5 79.2 480 25
MAXIMUM OPACITY, % 41.8 31.1 100 5
JUL91 # OF 0BS.= 65
CUMULATIVE EMI5SION TIME, SECONDS 46.0 29.7 170 0
MAXIMUM OPACITY, % 44.6 32.4 100 0
AUG91 # OF OBS.= 37
CUMULATIVE EMISSION TIME, SECONDS 40.6 22.8 116 0
MAXIMUM OPACITY, % 52.6 34.7 100 0
SEP91 # OF OBS.- 38
CUMULATIVE EMISSION TIME, SECONDS 40.5 18.9 81 0
MAXIMUM OPACITY, % 56.8 40.5 100 0
OCT91 # OF OBS.= 25
CUMULATIVE EMISSION TIME, SECONDS 49.7 46.2 259 14
MAXIMUM OPACITY, % 50.4 34.8 100 10
NOV91 * OF 0BS.= 16
CUMULATIVE EMISSION TIME, SECONDS 46.9 57.8 251 0
MAXIMUM OPACITY, % 56.9 39.4 100 0
B-13
-------
COKE OVEN TOPSIDE EMISSIOHS OBSERVATIONS STATISTICS
KIDC PUSHES
MONTHLY STATISTICS
AVERAGE
VALUE
STANDARD
DEVIATION
MAXIMUM MINIMUM
VALUE VALUE
OCT91 # OF OBS.= 63
CUMULATIVE EMISSION TIME, SECONDS 74.6 39.8
MAXIMUM OPACITY, % 78.7 25.9
329
100
41
20
NOV91 # OF OBS.= 34
CUMULATIVE EMISSION TIME,
MAXIMUM OPACITY, %
SECONDS
70.0
83.a
12.1
24.5
90
100
38
25
B-14
-------
Section 3
Quenched Coke Discharge £ Handling Emissions
Conventional vs. KIDC - Overall & Monthly
B-15
-------
QUENCHED COKE DISCHARGE/HANDLING EMISSION'S STATISTICS
CONVENTIONAL COKE
OVERALL STATISTICS
AVERAGE STANDARD MAXIMUM MINIMUM
VALUE DEVIATION VALUE VALUE
NUMBER OF OBSERVATIONS= 546
CUMULATIVE EMISSION TIME, SECONDS 2.3 8.6 121 0
MAXIMUM OPACITY, % 1.6 4.0 20 0
KIDC COKE
OVERALL STATISTICS
AVERAGE STANDARD MAXIMUM MINIMUM
VALUE DEVIATION VALUE VALUE
NUMBER OF 0BSZRVATI3NS= 166
CUMULATIVE EMISSION TIKE, SECONDS
MAXIMUM OPACITY, %
54.1 107.8 840 0
13.5 12.8 50 0
B-16
-------
QUENCHED COKE DISCHARGE/HANDLING EMISSIONS STATISTICS
CONVENTIONAL COKE
MONTHLY STATISTICS
AVERAGE
VALUE
STANDARD
DEVIATION
MAXIMUM
VALUE
MINIMUM
VALUE
MAR91 # OF OBS.= 35
CUMULATIVE EMISSION TIME,
MAXIMUM OPACITY, %
SECONDS 13.6 25.6
3.7 5.3
121
15
APR91 4 OF OBS.= 62
CUMULATIVE EMISSION TIME,
MAXIMUM OPACITY, %
SECONDS 1.4
0.6
5.8
2.9
34
20
MAY91 4 OF OSS.= 90
CUMULATIVE EMISSION TIME,
MAXIMUM OPACITY, %
JUN91 a OF OBS.= 60
CUMULATIVE EMISSION TIME,
MAXIMUM OPACITY, %
SECONDS 1.4
1.1
SECONDS 1.8
1.3
5.3
4.0
5.3
3.3
27
20
26
20
JUL91 # OF OBS.= 100
CUMULATIVE EMISSION TIME,
MAXIMUM OPACITY, %
SECONDS 1.8
1.5
4.5
3.3
22
2C
AUG91 * OF OBS.= 48
CUMULATIVE EMISSION TIME,
MAXIMUM OPACITY, %
SECONDS 3.7
2.3
5.a
4.3
17
13
SEP91 # OF OBS.= 75
CUMULATIVE EMISSION TIME,
MAXIMUM OPACITY, %
SECONDS 2.5
2.2
5.0
4.2
2C
15
OCT91 # OF OBS.= 37
CUMULATIVE EMISSION TIME,
MAXIMUM OPACITY, %
SECONDS 4.5
2.4
6.1
3.7
18
1C
NOV91 * OF OBS.* 19
CUMULATIVE EMISSION TIME,
MAXIMUM OFACITY, %
SECONDS C.O
Q.O
0.0
0.0
n-17
-------
QUENCHED COKE DISCHARGE/HANDLING EMISSIONS STATISTICS
KIDC PUSHES
MONTHLY STATISTICS
AVERAGE
VALUE
STANDARD
DEVIATION
MAXIMUM
VALUE
MINIMUM
VALUE
OCT91 # OF oas.- Ill
CUMULATIVE EMISSION TIME, SECONDS 66.5
MAXIMUM OPACITY, % 15.7
HOV91 # OF QBS.= 55
CUMULATIVE EMISSION TIME, SECONDS 29.2
MAXIMUM OPACITY, % 9.0
125.6
13.5
49.
10.
S40
60
264
45
B-18
-------
Section 4
Pushside Emission Observations Conventional S KIDC -Database
B—19
-------
HS
1
2
3
1
b
6
r
8
9
10
1 J
12
13
11
15
E6
1 7
18
19
2G
? 1
?2
tiS
?
3
4
5
6
8
0
1C
t t
1 2
13
14
15
16
17
ia
19
2C
21
PUSHER SlUt OVEN EMISSIONS OBSERVATIONS 10-50 Tuesday. Marcn jl, 1«92 1
DURING PUSHING OPERATIONS ONLY
KRI SS DEMONSTRAT ION PROjEC! - &E7HLEHLM S1EE- CQiiPORAIlON
SPARROWS POINT. MARYLAND
GBSfcRVfcKS
WIND
WltO
SPEED.
OBSERVER
DA ] b
BAITERY
INITIALS
WEATHER
CIRrCTION
MPH
LOCATION
03/26/91
11/12
S BP
OVERCAST
SL
10- 15
SOUTH
03/20/9!
1 1 / 1 2
SBP
OVERCAST
SE
10-15
SOlllH
03/2G/91
11/12
sap
OVERCAST
SE
10-15
SOUTH
03/26/91
11/12
SBP
0VERCAS1
SE
10- 15
SOUTH
03/26/91
11/12
SBP
overcast
sr
10- 15
SOUTH
03/26/91
11/12
SBP
OVERCAST
SF
10- 15
SOUTH
03/26/91
11/12
SfciP
OVERCAST
SE
10 15
SOUTH
03/26/9 1
t 1/12
SBP
0VFRCAST
SF
10- 15
SOUTH
03/26/91
11/12
SRP
OVFRCASr
SF
10- 15
SOUTH
03/26/91
11/72
SBP
OVfctfCASf
SF
10 15
SOUTH
04/O1/91
11/1?
SBP
OVERCAST
NW
10 1b
SOUTH
04/01/91
11/12
SBP
OVERCAST
NW
lO 15
SOUTH
04/01/9 1
11/12
SUP
ovlrcast
NW
10- 1S>
SOU I H
C.4/Cj 1/9 t
t 1/1?
SAP
0VER04SI
NW
10- 10
SOUTH
04/0 1/9 1
11/1?
SBP
OVERCAST
NW
10 15
SOUTH
01 /O 1/91
I >/ l?
S3P
OVERCAST
NW
10 15
SOU I H
04/0 1/91
1i/i?
S6P
OVERCAST
NW
10 10
SOU 1 H
04/O1/91
1 >/ f2
SEP
OVERCAST
NW
10 1Ii
SOU I H
04/01/31
11/12
SBP
OVfcKCASl
NW
•0- 1b
SOUTH
04/01/91
1 i / 12
SBP
OVERCAST
NW
10- 1b
SOUTH
04/10/9 1
11/12
H
35
CHFMICC
1?4ft
1? 10
95
40
CHEMICO
1258
12 : 23
82
25
CHFMiro
1?G8
12.35
85
30
CHEMICO
1121
12:50
85
S'j
CMfcWlCO
1 131
13 r 0 1
85
20
CMPMirO
1 1O0
1.1 11
9b
45
rusHto TWICE
CHLMICO
1151
13 : 23
8b
50
CHEMICO
117 1
13: 37
ao
10
C'HhMtCO
1 10 1
13 : 50
90
4:j
SHENANGO
1236
11:43
/t
4 b
SHENANGO
1 2 4 li
1 1 u2
80
25
Shfnango
1s SB
12 14
70
?0
SHENANGO
12 bb
12 . 23
75
50
SHtNANGC
1 101
13.24
75
40
SHENANGO
11 :> 1
11: 35
80
15
SilLNANGU
1 131
13. 52
70
5
SHENANGO
1 11» 1
14.01
15
35
a# f NO PUSH
SHENANGO
117 1
14:11
75
15
SHENANGO
1201
14 : 28
10
100
» END PUSH
S'IFNANGQ
i r-4 j
i 1 20
Cb
70
SHFNANGO
1 108
11:40
82
40
background
BATTI-RY
RAIFFRY
-------
IBS
23
24
25
26
27
28
29
30
3 1
32
33
34
:u">
36
37
¦j b
39
40
4 1
42
4'J
AA
IBS
23
2 4
25
26
2 7
2fa
29
30
3 1
32
33
3 A
36
36
37
3ft
39
40
4 t
42
43
44
PUSHER SIDE CJVrN FMISSiCNS OBSE RVA F1UNS 10. 50 Tuesday, March 31. 1902 2
DURING PUSHING OPERATIONS ONLY
KRESS DEMONSTRATION PROJECT BETHLEHEM STEEL CORPORATION
SPARROWS POINT, MARYLAND
L)A i E
04/10/91
04/ 10/91
04/10/91
04/10/91
04/lO/M1
04/10/91
04/lO/JM
04/15/01
04/15/91
04/15/01
04/15/91
04/lb/91
04/15/9'
04/15/01
04/15/91
04/ 1t> / <4 1
0-1/15/91
04/24/91
04/24/01
04/24/91
04/24/91
04/2 4/91
fc MISSI ON
CUNIKOL
SYSItM
shfnango
SHFNANGO
SHENANG0
SH*MANGO
SHf-NANGD
SHfc NANliU
SHFNANGO
bHbNANGO
SHtNANGO
SHtNANGO
SltCNANGO
SHf-NANGU
SHtNANGQ
SHENANGO
SHENANGO
SHFNANGO
SHENANGO
CHFMICQ
CHEMi CO
CHtMICQ
CHEMICO
CHEMICU
OBSERVERS
wiNn
SPFtn,
HRSERV
13 A1 TCRY
INITIALS
WEATHER
D 1 NEC I ION
MHH
I OCA I I
1 1/12
f RC
OVERCAST
MW
1A
SWlST
11/12
FRC
OVERCAST
NW
tii
SWt-Si
11/12
FRC
. overcast
NW
18
swfcsr
11/12
FRC
OVFRCAS T
NW
IS
SWfcSI
11/1?
FRC
OVERCAST
NW
18
swest
11/12
f-RC
OVERCAST
NW
18
SWEST
11/ 12
FRC
OVERCAST
NW
10
3 W l 3 T
11/12
SOP
RAIN
SE
i»
O
SOUTH
11/12
SBP
RAIN
SE
&-
0
SUUIH
11/12
SUP
RA IN
SL
b-
o
SOU 1 H
M/12
SBP
RAIN
St
5
o
SOUTH
1 1/ 12
SUP
RAIN
SE
5-
o
SOUTH
M/12
SKP
R A IN
Sf-
S -
o
SOUTH
1 1/12
sep
RAIN
sc
5
0
SOUTH
11/12
SBP
RAIN
5f
b *
0
SUUIH
M/12
SOM
RA IN
St
S
0
SOUTH
11/12
SBP
RAIN
sr
5 -
o
SOUTH
11/15
SRP
OC/RAIN
St
io-
1b
S0U1 H
11/12
SRP
OC/RAIN
5C
10
<5
SOUTH
11/12
SBP
oc/rain
SE
io-
15
SQLIH
1 1/ 12
SBP
QC/KA1N
St
io-
1 b
SOUTH
11/12
SRP
(IC/RAfN
Sf"
10-
'K
SOUTH
CUMULAJIVk
1 1Mb
I I ME lib
MAXIMUM
UVtiSi
Oh
SOUHCfc UY
tMISSIONS
OPACITY
NUVBbW
DAY
tMISSIONS
SECONDS
%
COMMENTS
1206
J
54
63
60
1216
12
09
67
60
1226 *
12
15
74
70
12 3«
12
26
7 1
£5
1246
12
39
66
65
114B
12
*j6
79
7 b
1 1 SB
13
10
66
25
1 126
1
4 3
1 10
65
12'Jfe
12
Q'J
7t>
*'* b
12 10
12
23
135
lOO
1226
12
33
1 15
KM)
1236
12
4b
RO
too
1 24(>
12
58
ftO
30
I25C
13
oa
15
15
1 148
13
3d
20
1b
I20fi
13
* 4
25
10
1248
14
03
15
15
1 206
12
48
^0
35
1? 16
13
02
70
100
12 2 b
13
1 1
70
10o
1236
3
24
ao
IOC
1246
13
33
90
25
BACKGROUND
BATTtKY
BAI IERY
BATTkRY
BATTERY
BA f1ERY
BATTERY
UATTLRY
-------
45
46
47
48
'19
bf;
51
5 2
53
54
55
56
57
55
00
6 1
h'J
63
64
65
66
IBS
45
4b
47
46
49
50
b 1
52
5 "J
~j-l
bb
56
«j7
5 ft
59
€0
G1
62
63
64
61i
€6
PUSHER SIDE OVEN EMISSIONS OBSERVATIONS 10:50 Tuesday. March 31, 1992 3
UUKING PUSHING UPLNAT lON'j ONLY
KRCSS DEMONS f RATION PROJECT - BETHLfHFM STrM CCWPORAfJON
SPARROWS POINT. MARYI AND
WINO
OBSERVERS
WIND
SPffO,
OBSERVER
OATE
BATTERY
INITIALS
WEATHER
DIRECTION
MPH
LOCATION
04/24/91
11/12
S BP
OC/RA
IN
SF
IO- 15
SOUTH
04/2-1/91
11/12
SBP
OC/RA
IN
SF
10- 15
SOUTH
04/24/91
11/1?
SRP
OC/RA
IN
SE
10 15
south
04/24/91
1 t/ 12
SBP
OC/RA
IN
Sfc
10- 15
SOUTH
04/24/91
11/12
SBP
OC/RA
IN
SE
10 15
SOU I H
04/29/a 1
11/12
SBP
HC/RA
TN
SF
7-1?
SOUTH
04/29/91
11/12
SRP
OC/Ra
rN
SE
7- 12
south
04/29/H1
11/12
SBP
CU:/RA
IN
St
1 11
SOUTH
04/20/01
11/1?
SBP
OC/Ra
IN
SL
7 12
S0U1 H
04/20/91
11/12
SBP
OC/RA
IN
SE
7 12
SOUTH
04/29/01
1 1/12
SBP
OC/RA
IN
SE
7 1 -J
SUUiH
04/29/91
11/12
SBP
OC/RA
IN
SF
t IV
SOUTH
04/29/91
11/12
SBP
OC/RA
IN
SL
' 12
SUUIH
04/29/01
1 1/12
SBP
OC/RA
IN
SL
7 12
S0U1 H
04/29/91
11/12
SUP
OC/RA
IN
SE
7- 12
SOU i H
Ob/00/9 1
11/12
SUP
RAIN
SOUTH
G 10
SOU 1 H
O'o/Ot)/91
1 1/1?
SBP
WAIN
Mill 1 H
I lO
SOUI H
o'j/ofa/y 1
11/12
SHP
RAIN
SOU I H
b- 10
SOUTH
0b/O6/91
11/12
SBP
RAIN
SOU 1 H
b- 10
SOUTH
05/06/91
1/12
SBP
RAIN
SOUTH
5 lO
SOUTH
05/06/91
1 1/12
SRP
RAIN
SOUTH
5- 10
SOUTH
05/06/91
11/1?
SBP
RAIN
S0U1H
5- 10
SOUTH
CLMULAI1Vc
EMISSION
T I ML
TIME OF
MAXIMUM
CONTROL
OVEN
OF SOUKCt Uf
EMISSIONS
OPACI IY
SYS 1 EM
NUMBER
DAY EMISSIONS
SECONUS
%
COKVENl'S
BACKtiROUNO
CHFMICO
1 1 48
14 03
7b
b
CHEMJCI1
1208
14 17
K5
h
CHEMICO
1228
14 : 26
10
20
CHEMICO
1238
14 : 33
65
100
CHEMICO
1248
14:41
60
fiO
SHENANGO
1256
13 OA
90
7 b
SHENANUO
1 148
13 . 27
1 10
lb
SHENANGO
1200
13 42
8 b
10
SHENANGO
1238
13:4$
6 b
100
Sill NAN(iU
»24H
U (X>
10
so
thenango
r?50
i-1 12
65
35
SHENANGO
l?GB
14 . 20
fto
60
shlnamoo
1 10 1
14 b 4
65
100
SHf- NANOf)
1131
15- lO
20
20
SHENANGO
I lb 1
1 b : 19
80
15
CHEMICO
1 102
11:45
OO
100
CHEMICO
1 152
11 . r>a
8 b
10
CHEMJCO
1172
12 ; 15
60
too
CHEMICO
1229
12:27
70
5
CHEMICO
12 12
12-55
20
fiO
CHcMJCO
1222
13: 11
70
70
CHEMICO
1232
13:13
5
15
-------
IBS
G7
68
69
70
71
72
73
74
75
7G
77
7 ft
79
30
ai
82
83
84
8b
tfb
87
as
IKS
67
6*
69
70
7 1
72
73
74
75
7G
77
7ft
70
80
ai
82
83
84
85
86
87
88
UA I f
05/0G/91
05/06/91
05/0G/9 1
os/ i'j/a i
Ob/13/91
Ob/ 13/9 1
05/13/91
05/>3/9 I
05/13/01
05/13/91
05/ 13/91
Oh/ 13/9 1
05/13/91
OS/2 1/9 1
OD/21/91
Ob/2 1/9 I
OS/2 1/9 t
05/21/91
05/2 1/91
05/2 1/91
0b/2t/SM
Ob/2 1/91
FMT5SION
CONTROI
SYSTFM
ChtMICP
CHCMICO
CHESHICO
SHENANGO
SHENANGO
SHENANGO
SHENANGO
SHENANCO
5IICNANG0
SHENANGO
SHfNANC.n
SHENANGO
bHfc NANGO
CHENANGO
SHENANGO
5HCNANG0
SHENANGO
SHENANGO
SHENANGO
SHENANGO
SHENANGO
SHENANGO
PUSHER SIDE OVFN FMTSS7DNS OBSERVATIONS 10:50 Tuesday. March 31. 1992 4
DURING PUSHING QPERAIIONS ONLY
KRFSS DEMONS rRATT0N PRCJ.JFCT - KFTH1FHI-M STEF_ CORPORATION
SPARROWS POINT, MARYLAND
1/12
1/12
1/12
1/12
1/12
1/12
1/12
1 / 17
3:23
70
1CC
1 147
1 1 40
VQ
7 b
1245
12 03
fcb
55
I2b5
12 -JO
IO
20
70 SEC PUSlt
1 167
12 4 1
2b
30
75 SFO PUSH
1207
13 04
3b
50
75 SFC PUSH
'.217
13 1b
SO
75
1237
1331
80
too
1247
13 44
2 b
20
7b SFC PUSH
1 207
13 . 54
70
ICO
-------
PUSHER SIDE OVEN EMISSIONS OBStRVAT IONS 10; 50 Tuesday, March 31, 1992 fj
DURING PUSHING OPERATIONS ONLY
KKI-SS DEMONSTRATION PROJECT BETHLEHEM STEEL CORPORATION
SPARROWS POINT. MARVT AND
WIND
OBSt RVtKS
WIND
SPEED.
OBSfRVGR
DBS
DA lb
BAULKY
INITIALS
WEATHER
DIRECTION
MPH
LOCATION
BACKGROUND
ay
05/21/91
1 1/12
SBP
Ct EAR
SF
5- 10
SOUTH
90
Ofc/03/91
11/12
Slip
RAIN
NE
5 10
SOUTH
3 t
06/03/91
11/12
StSP
RAIN
NC
5 1 o
SOl 1 H
92
06/03/91
11/12
SBP
RAIN
NF
5- 10
SOUTH
93
06/03/91
1 1/12
SBP
RAIN
NE
5 10
SOUTH
94
0b/03/91
11/12
SBP
RAIN
NE
5- 10
SOUTH
9 b
06/03/91
1 1/12
SBP
RAIN
NE
5 10
SOUTH
96
()b/03/91
11/12
SBP
RAIN
NF
5 - 10
SOUTH
97
06/03/9 1
1 t/ t2
SfiP
RAIN
NC
b 10
SOUTH
98
06/03/91
11/1?
SRP
RAIN
Nfc.
5 10
SOUTH
99
06/03/9 1
t 1/12
SHP
RAIN
NE
5 10
SOUTH
100
07/O1/0\
1 1 / 1 2
SRP
overcast
NL
1(» - V.,
SOU 1 H
BAITERY/SKY
101
0?/0l/fl1
1 1/12
SBP
OvrRCAST
Nc
10- 1b
SOUTH
BA1TFRY/SKY
102
07/01/91
11/12
SBP
OVERCAST
NF
K>- 1b
SOU 1 H
BAITERY/SKY
103
07/01/91
1 1 / 1 ?
SRP
OVfRCAST
N€
to- 1S
SOU! H
BATTERY/SKY
104
07/01/91
11/12
SBP
OvCRCAST
NL
to 1b
SOUTH
BAITERY/SKY
1 Oh
07/0 1/H 1
1 1/13
SBP
OVERCAST
NL
10 lb
SOUTH
fiAT)FRY/SKY
ICG
07/01/91
11/12
50P
OVfRCAS1
NF
10- lb
SOUTH
BATTERY/SKY
107
07/01/91
11/12
SOP
OVtRCAS?
Nt
10- 15
SOUTH
BATTERY/SKY
ICQ
07/O1/91
11/ i -J
SUP
OVt-KCAST
Nh
10- 15
SOUTH
RAT TFRY/SKY
109
07/01/91
11/12
SBP
OVhRCAST
NL
10 15
south
BATTERY/SKY
1 10
07/O&/91
11/12
SBP
CLhAR
WL ST
lb ?0
SOUTH
BAIIfcRY/SKY
COMULATIVl
EMISSION
T
i MF
TIME OF
MAXIMUM
CONTWni
dvfn
OF
SOURCE OF
EMISSIONS
OPACITY
UBS
SYSTfeM
NUMB feM
DAY
EMISSIONS
SECONDS
%
COMMENTS
39
SHENANGO
1111
14
13
lb
30
90
SHENANGO
1 1 35
1 1
: 29
/ b
100
91
SHENANGO
1 153
1 1
49
40
15
70 SEC PUSH
92
5HCNANG0
1223
12
00
20
100
110 StC PUSH
93
SHkNANGU
u>33
12
16
90
ICC
91
SHENANGO
1243
f 2
32
90
30
yb
SHtNANGO
120b
12
: 47
10
20
70 SEC PUSH
9b
ijHk-r4ANt:u
i:i
01
14 5
ICO
PUSHED 3X
97
SHfcNANGO
12 1b
13
3b
SO
45
96
ShtNANGQ
1 2 2 b
13
bG
7 5
ICO
99
SHENANGO
• 235
14
00
PO
OS
ICO
SHI-NANGO
1 i S I
1 1
19
DOOR
55
ICO
10 I
SHkNANGO
•. i :t s
t 1
:> i
DOOR
35
100
1C?
CHENANGO
1 r> 3
t 1
¦13
fiOOR
I fj
10
103
SHENANGO
i 126
1 1
. 56
OCJOR
70
75
104
CHENANGO
1 236
1?
17
OOOR
i>b
100
105
SHFNANGO
1 ?4o
12
: 2 4
DOOR
40
60
106
SHI-NANGO
1?0S
12
:46
DOOR
70
2b
»G7
SHENANCO
i?2B
1 3
: 01
UOOR
85
45
ica
SHENANGO
123fl
13
12
DUUW
80
100
109
SHFNANCO
1 ?AB
13
19
DOUR
25
15
1 10
SHENANGO
1 1b1
1 1
1G
DOOR
20
25
-------
OKS
1 1 1
1 12
t 13
t 14
t t b
1 16
I IV
1 18
1 19
1?0
12 1
122
i?n
12-?
I 25
1?fi
127
12 b
129
130
13 1
U2
OBS
\ 11
1 12
1 13
J 14
1 15
1
I 17
I IB
1 19
t?0
12 *
122
123
124
125
126
127
128
129
130
131
132
PUSHER Sine OVEN EMISSIONS OBSERVATIONS 10:50 Tuesday, March 31. 1992 6
DURING PUSHING OPERATIONS ONLY
KRESS DEMONSTRATION PROJECT BETHLEHEM STEEL CORPORATION
SPARROWS POINT, MARYLANO
WIND
ORSERVl
RS
WIND
SPEED,
OBSERVER
DA 1 t-
HA 1 IfrHY
INIT IAI 5 WtrATHffft
Ul RFC.T ION
Mf>H
1OCATTON
R ACKf.ROi ;NH
07/03/01
11/12
SOP
CLEAR
WEST
15 20
SOU Tit
DAT TCRY/SKY
O7/08/91
1 1/12
SOP
CI FAR
WEST
15-20
SOUTH
BAT fERY/SKY
07/03/91
11/ 12
SBP
CI EAR
WEST
15 20
SOUTH
BAT(ERY/SKV
07/08/91
1 1/ 12
SBP
CLEAR
WEST
15-20
SOUTH
DA 1TERY/SKY
07/08/91
11/12
SBP
CLEAR
WEST
15 20
SOUTH
OA!TFRY/SKY
O7/08/91
11/12
SBP
CLEAR
WLS1
1 b - 20
SOUTH
RAT 1fcRY/SKY
07/08/91
1 )/ 12
SBP
CI FAR
WEST
15-20
SOUTH
BATTERY/SKY
07/08/91
11/12
SBP
CLEAR
WfcSI
1 b - 20
SOU I H
BAT 1ERY/SKY
07/08/91
11/12
SBP
CLEAR
WEST
15 ?0
SOUTH
BATTERY/SKY
07/15/31
11/1?
SRP
rI FAR
NF/SE
S-10
SOUTH
BATTERY
07/15/91
11/1?
SBP
CLEAR
NF/SE
5- 10
SOUTH
BATTERY
07/IS/91
11/12
SBP
CLEAR
NC/SC
5 10
SOUTH
BAT 1LRY
07/15/91
11/12
SBP
Ct EAR
MVSC
5 10
SOUTH
BAT IERY
O / / 1 'j / 9 1
1 1 / 12
SBP
CLEAR
NE/SE
'j- <0
hOUIH
BA i TEKY
07/15/91
11/12
SBP
CLEAR
NE/SE
S 10
SOUTH
BATTERY
07/ 1 ft/a 1
11/1?
SRP
CI FAR
NF/SF
5-10
south
BATTERY
O// '5/91
11/1?
SBP
Ci EAR
NE/SE
5- 10
SCUIH
BA1 IERY
07/15/01
11/1?
SOP
CLEAR
NE/SE
5 "O
SOUTH
BATTERY
07/15/91
1 1/ 12
SBP
CLCAR
NC/SC
5 10
SOUTH
BAT I FRY
o / /'J'A /y 1
11/12
SHP
CI EAR
SE
15 - 20
SOU 1 H
BA1 F ERY/SKY
07/22/91
1 1/ 12
SBP
CLEAR
Sfc
1 1j - 20
SOUTH
RATTFRY/SKY
07/22/91
1 1/ 12
SBP
CLEAR
SE
15-20
SOUTH
BATTERY/SKY
CUMiif ATIVE
rMISSION
I 1Mb
TIME oe
MAX I Ml JM
rONTROI
OVFN
OF
SOURCE OF
F-HI SS J0\S
OPACITY
SYSTEM
NUMBER
OAY
EMISSIONS
SECONDS
%
COMMENTS
SHENANGO
1 135
11.31
i;uun
3b
KM)
90 SEC PUSH
SHENANGO
1153
1 1 : 40
DOOR
?5
35
SHENANGO
1226
1 1 : S4
OOOR
5b
45
180 SEC PUSH
SHENANGO
1236
12 :08
DOOR
35
•oo
SHE NANC10
1246
12:21
DOOR
80
?0
SHENANGO
1265
1 J • 38
DOOR
?o
15
85 SEC PUSH
SHbNANGO
i?oa
1? 52
DOOR
6h
SHENANGO
1238
13 02
DCOR
80
•oo
SHENANGO
1?48
13 11
DOOR
15
55
SHtNANGH
l?3?
1 1 • 5G
crop
?•-
?0
S5 SEC PUSH
^He NANC.U
1 1S 1
17: 1 3
OOOR
15
10
SI tCNANGO
1 135
12.31
DCOR
70
100
SHfcNANGO
I 153
12 : 37
OCOR
10
5
SHFNANCO
1 168
1? 4G
DOOR
05
10
i k AM^S
SHENANGO
1242
13 04
COO*
75
20
SHENANGO
121*2
13:11
DOUR
20
85
Smenangu
1272
1 3 : 2u
DC'OR
50
25
SHENANGO
12 14
1 3 ; 4 4
DOOR
7 b
45
SHENANGO
1224
13 52
DOOR
15
jo
SHENANGO
1 140
11 2 3
DOOR
71;
lOO
S/1'.NANGO
1 151
1 1 .51
DOOR
80
25
SHENANGO
1135
12.1b
DOUR
3b
100
-------
PUSHER SIDE OVCN LMI5SI0NS OUSCRVA 1 i3NS IQ.bO Tuesday, March 31. 1992 7
DURING PUSHING OPERATIONS ONI 1
KRFSS DEMONSTRATION PROJECT - BfclHlEMLM STCFl CCRPORAIION
SPARROW* PtJINI , MARVIAND
w 1 NO
OBSERVERS
WIND
SPEED.
OBSERVER
OKS
OATf
8A I tLHY
INIJJALS
WtAIMER
DIRECT ION
kph
L0CA1ION
BACKGROUND
133
07/22/91
11/12
sap
Ci FAR
Sh
1^-20
SOUTH
BATTERY/SKY
13 4
07/22/9 1
11/1 2
SBP
Ci tAR
SE
15-20
SOUTH
pattery/sky
13 b
07/22/81
t 1/12
SBP
CLEAR
SE
15 20
SOUTH
battcry/sky
1 3b
07/22/91
11/12
SBP
CLtAR
St
15-20
SOUTH
BATTERY/SKY
137
07/22/9 1
1 1 / 1 2
sbp
C< EAR
SF
15-70
snui H
BAT Trwv/SKY
138
0 7/22/91
11/1?
SRP
CI FAR
SF
15-20
SOUTH
BAITERY/SKY
139
07/22/91
11/12
SBP
Ci FAR
SE
lb 20
SOUIH
EA1T ERV/SK1
1 40
07/:»2/9 1
11/1?
SHP
CA f- AR
SF
15-20
50U1H
OA!TERY/SKY
14 1
07/29/91
1 1/12
GW
OC/RAIN
NE
5 10
SOUTH
CLOUDY
14?
07/29/9 1
It / 1 ?
GW
OC/RAIN
NF
bio
SOU 111
CI IJUUY
143
07/?3/91
11/12
GW
OC/RAIN
NE
5- 10
SOU J H
Ci 0UDY
1 44
07/29/9 1
11/1?
GW
OC/RAIN
Nt
b- 10
SOUTH
CLOUDY
145
07/29/9 1
11/12
GW
OC/RAIN
NL
5 K)
SOUIH
ct onnv
1 46
07/29/91
11/12
REA
RAIN
t AS!
10
SOUIH
RAT I ERY/SKY
147
07/2D/9 1
11/12
RLA
RAIN
LAS I
10
SOU 1 H
HA I rfcRY/SKY
MH
L»'/29/y 1
11/12
Kh A
RA IN
ASI
10
c»OUTH
BATTERY/SKY
119
07/29/91
11/12
RF A
RAIN
LAS I
10
SOU I H
RAT TERY/SK
15(J
07/29/9 1
11/12
RE A
RA J N
I ASI
10
SOUTH
BATTf RY/SKf
15 1
07/29/9 1
11/12
SBP
RAIN
EAST
S- 10
SOUTH
HATTFRY/SKV
152
07/29/91
11/12
SHP
RA IN
FAST
5- 10
SOUTH
BATTERY/SKY
153
0//29/91
1 1/12
SBP
RAIN
EASI
5- 10
SOUTH
BATTERY/SKV
154
07/29/9 1
11/12
SBP
PAIN
car. t
5 in
SOUTH
BA 1 1 fcRY/SKY
CUMULA 1 VE
EMISSION
riMk
TIME 0*
MAXIMUM
CONTROL
OVEN
OF
SOURCE OF
EMISSIONS
OPACITY
OBS
SYSTEM
NUMBER
OAY
EMISSIONS
SFCONDS
%
fOMMFNTS
133
SHTNANCn
1 153
1 7 : 30
DOOR
50
dG
134
SHENANGO
1222
12 42
DOOR
1b
10
135
5HENANG0
1229
12:50
DOOR
30
20
STICKLR
136
r>HFNANG0
1232
13 CO
fjfJOR
20
30
137
SHENANGO
1242
13: 14
DOOR
45
25
138
5HEMANGO
12C2
13 . 23
DOOR
5 b
55
133
SHENANGO
1272
1 3 3b
DOOR
70
45
65 src push
140
SHENANGO
12 14
13 4b
DOOR
70
G5
M I
SHENANGO
1242
S3 10
DOOP
20
20
QA/OC
1-1?
SHFNANGO
126?
13 17
DOOR
24
05
GA/OC
143
SHENANGO
1272
•3:27
DOOR
124
3C
QA/OC
144
SHfcNANGO
1 168
1 3 40
DOOR
3 /
10
QA/OC
145
shenangq
12 14
14 09
OOOR
105
SO
OA/OC
14G
SHENANGO
124 2
13 . 10
DOOR
20
25
GA/OC
147
SHfcNANGO
12fc>2
13 17
COOP
20
55
OA/OC.
148
SHENANGO
1272
13:27
DOOR
122
3C
QA/QC
149
SHENANGO
1 168
13 40
DOOR
40
4b
QA/QC
1SC
SHENANGO
1214
11 08
DOOR
1 10
5C
OA/QC
151
SHENANGO
1242
13-10
DOOR
20
25
QA/OC
152
Si ItNANGO
12tt2
13 17
DOOR
20
55
QA/OC
ib:i
SHfcNANGO
1272
13 27
DOOR
122
30
QA/QC
154
SHfcNANGO
1 1 SB
13:40
DOOR
40
45
QA/OC
-------
oos
155
156
157
158
159
160
1G1
162
163
164
165
166
167
168
ir,s
170
171
1 /*>
17:*
174
! 7b
176
0B5
1bb
156
1b 7
108
159
160
161
162
16 J
164
16'j
! GG
167
168
169
17 C
1 i 1
1 7 2
1 fJ
174
1 7 ft
1 76
PUSHtR bll)F OVFN EMISSIONS 0BSERVA1I0N5 10:50 Tuesday, March 31. 13S2 8
DURING PUSHING OPERATIONS ONi <
KRESS DEMONSTRATION PROJECT BETHLEHEM STFfi CORPORATION
SPARKOWS POINT. MARYLAND
I NP.
OBSERVERS
UM Uf)
SPFfO.
OBSERVER
DA IX
BATTEKY
1NI1IALS
WEATHER
DIRECTION
MPH
I OCA1 ION
BACKGROUND
07/29/9 t
11/12
SBP
RAIN
EAST
5 ¦¦¦¦
10
SOUTH
RATlERY/SKY
07/29/9 1
11/12
sen
RAIN
LAST
5
10
sum h
BA i TERY/SKV
07/29/9 1
11/12
SBP
RAlM
EAST
5
10
SOU 1 H
BATTERY/SKY
07/29/91
11/12
SRP
RAIN
EAST
b
10
sou in
BA!TfcRY/SKY
07/29/9 1
11/12
sop
RAIN
fcASI
5 -
10
SOUTH
GATTrRY/SKY
07/29/91
11/12
SEP
RAIN
CAST
5-
10
SOUTH
BATTERY/SKY
oe/oi/9i
11/12
SOP
CLEAR
st/w
7-
12
SOU I H
BATTERY/SK?
08/01/91
11/12
SRP
CI FAR
SE/w
12
SOUTH
RAT IF RY/SKY
OB/OI/91
1 1/ 1?
SRP
clear
SE/W
12
SOUTH
BATIERY/SKY
08/01/91
1 1/12
snp
CI FAR
st/w
7
12
SOUTH
BAT IfcRY/SKY
08/01/91
11/1?
SBP
CLEAR
SE/'W
7 -
12
SOUTH
BATIERY/SKY
08/Ob/91
11/1?
SRP
clear
NW
10
1b
SOUTH
0ATTERY/3KY
OB/Ob/91
1 1/12
SRP
CLEAR
NW
10
1 b
SOUIH
BA i TfcRY/SKY
08/05/9f
H / 1 2
SBP
ClTAR
NW
10
15
SOU (H
BATIfeKY/SKY
08/05/91
11/12
SBP
CI EAR
NW
10
lb
SUU I H
BA 1 TERY/SKY
08/05/91
i 1/12
SRP
CI EAR
NW
10
- lb
SOUTH
BATTERY/SKY
08/05/91
11/12
SRP
CLEAR
NW
JO
- 1b
SOUTH
BATTERY/SKY
0B/05/91
11/12
SRP
CLLAR
NW
10
1b
SOUTH
OA 1TERY/SKY
voa/os/nt
11/12
SUP
CLCAR
NW
10
- !b
SOU I H
BA f ffcRY/SKY
03/05/91
11/12
SBP
CLEAR
NW
10
15
SOUTH
BATTERY/SKY
Ofl/Ob/9}
11/1?
SRP
CLEAR
NW
10
15
SOU111
BA! 1 tRY/SKY
08/12/9 1
11/12
SBP
CS FAR
SOUTH
5
10
SOUTH
BATTERY
CUMULA T I VI
EMISSION
TIME
TIME OF
MAXIMUM
CONTROL
OVEN
UF
SOURCE Uf
LMISSIUNS
OPACITY
SYSTEM
NUMBER
DAY
EMISSIONS
SECONDS
%
CGMMEN1S
bi ItNANGU
12 14
14 0«
DOOR
t 10
SO
QA/QC
SHENANGO
i '.Ol
14 2 1
door
80
100
SHtNANGO
1224
14 : 35
DOOR
85
70
SHENANGO
1234
14 43
DOOR
90
ftO
SHENANGO
154-1
14 53
nnnp
55
65
oo sec push
SHENANGO
1216
15 08
nnoR
7*
3b
KIDC
1 118
1113
nnnff
52
4 =
SHENANGD
1 1 35
1 1 23
DOOR
54
100
HEAW SMOKE
K IDC
I 1j 1
1112
DOOR
no
100
SHE NANGO
1 22 2
f 1 57
DOOR
19
100
SHENANGO
1 1S3
12 06
DOOR
39
15
SriENAfyGO
1 ' 10
1 J 'J 3
DOOR
20
ShFNANGn
1 1r>i
1? 10
DOOR
34
35
HVV SMOKE
S~ltfMANGU
1 1 i'l
1? 32
DOOR
5?
100
HVY SMUKt
shenango
i ib3
12 40
DOOR
C*
50
HVV SMdKt
SHENANGO
12 17
13 00
DOOR
25
10
HVV SMUKE
SHfcNANGU
1229
(3 09
DOOR
17
20
STICKER
SHENANGO
1237
13 ~4
DOOR
8 1
lOO
HVV SMOKE
SHENANGO
1247
13-40
door
6
5
CHENANGO
1113
14 0?
OflOR
03 v
70
SHFNANC.O
1 ?C9
14 : 18
DOOR
12
10
SHENANGO
I 135
11:31
DOOR
45
100
-------
UBS
177
178
179
180
18 1
182
183
184
165
186
IB7
1 fiH
18H
190
191
192
193
194
19b
196
197
198
OBS
17?
178
1?9
180
18 1
182
183
184
18h
186
187
168
1 P. 9
190
1S1
19?
193
194
195
19b
197
198
PUSHER SIDt OVFN EMISSIONS OBSERVATIONS 10:50 Tuesday, March 31, 1992
DURING PUSHING OPERATIONS DMI V
KRESS DEMONSTRAI ION PROJECT - RETHLFHEM STTT . CflRPORATION
SPARROWS POINT, MARYtAND
WiNU
OBSERVERS
WIND
SPI-bO ,
OBSERVER
~ Alt
BATTERY
INITIALS
WEATHER
DIRECTION
MP-I
LOCATION
BACKGROUND
08/12/91
1 1/ 12
SBP
CLEAR
SOUTH
b 10
SOUTH
BAIItHY
03/12/91
1 1/ 12
SRP
CI F AR
SUIIIH
5- 10
SOUTH
BAT ILRf
08/12/9 1
11/12
SBP
CLEAR
SOUTH
b 10
SOUTH
BA1ILKY
oa/14/91
11/ 12
SBP
OVERCAST
SW
15-20
SOUTH
BATTERY
08/ 14/91
11/ 12
SBP
OVFRCAST
sw
15-20
SOUTH
OA I 1ERY
OH/14/91
1 1/ 12
SRP
OVFRCAST
SW
15 20
SOUTH
BAT 1 ERY
08/14/91
11/12
SBP
overcast
SW
-,5-20
SOUTH
BAT I CRY
08/14/91
11/12
SBP
OVFRCAS1
sw
1b 20
SOUTH
BATTERY
08/14/91
11/12
SBP
OVFRCAST
SW
15-20
SOUTH
RAT 1ERY
08/ 19/91
11/12
SBP
OVERCAST
NW
10 15
SOUTH
BA 1 fcRY
oa/ iry/91
1 1/ 12
SOP
OVCRCAST
NW
lO 1b
SOU 1 H
BAITER/
08/ 19/91
11/17
SBP
OVERCAST
NW
10- 15
SOUTH
BAI!fcRY
OH/ 111/91
11/12
SOP
OVERCAST
NW
10*15
SOUTH
BAT 1 FRY
Oil/ 1 U/9 1
11/12
SHP
OVERCAST
NW
10 1 b
SOUTH
BATTFQ/
08/19/91
11/12
SBP
OVERCAST
NW
'.0- lb
SOU I H
BAITERY
00/ 19/9 1
11/12
SBP
UVtRCASf
NW
10- 1b
SGUTH
BATTERY
08/19/91
11/12
SKP
OVERCAST
NW
10- 15
SOUTH
BATTER/
08/19/91
11/12
SKP
OVFRCAST
NW
10- 15
south
BATTERY
08/19/91
11/12
SBP
overcast
NW
10-Ib
SOUTH
BATTERY
08/26/91
1 1/12
SRP
OVFRCAST
sr
10 15
SOUTH
BATTERY
OA/26/91
1 1/12
SBP
OVERCAST
SE
10-15
SOUTH
BAITfcRY
00/26/91
1 1/12
SOP
UVERCAS1
si-
10 - 1 b
SOU TH
BATTERV
CUMULATIVE
FMTSSION
TIME
TIMfc or
MAXIMUM
CONTROL
QVtN
OF
SOURCt OF
EMISSIONS
OPACITY
SYSTEM
NwMGCR
DAY
CMISS1UNS
SECONDS
%
COMMEN1S
SHENANGO
1 Is 1
11:47
DOOR
1 13
80
SHENANGO
1201
1203
DOOR
50
If!
SHENANGO
1 153
12:21
DOOR
32
35
SHENANUO
1208
13.0b
UOOR
42
25
SHENANGO
1248
13 : 20
OOOR
12
65
SHCNANGO
!2b8
13. an
uunw
48
bO
SHENANGO
1268
13.51
DOOR
2 6
40
SHENANGO
1201
14 15
nnoR
33
15
SHtNANGO
1? 1 1
14 :P3
DOOR
8
CHFMICO
1 1.15
1 1 1G
DOOR
52
V'j
CHtMlCO
12 17
1 1 : 26
odoq
42
35
PUSH3X STKR
CHEMICO
» 148
1 1 . 3H
DOOR
23
45
CHEMICO
1 1 b 1
12 .08
DOOR
86
40
CHEMI CO
1 1 b'J
12 26
DOOR
63
1O0
CHEMluO
12 3b
12 . A J
ouor
4b
lOO
CHFMICO
1246
12 • 50
DOOR
3C
1 b
f.HFMirn
1200
13 02
DOOR
A 1
2b
CHEMICO
I23H
1 A 1 4
OOOR
72
100
CHEMICO
1248
13 2?
DOOR
5 1
3b
SHENANGO
1 148
1117
DOOR
62
40
SHfcNANGO
1 13b
1 1 ; 38
DOOR
14
no
SHENANGO
1 lb 1
1 1 47
onnR
76
85
-------
OBS
193
200
201
i> 02
203
204
205
206
207
208
209
2 10
2 I 1
2 12
2 13
2
2 1 b
2 16
2 1 V
2 18
2 19
220
OBS
199
200
201
202
203
204
205
7 Of,
2(>7
20a
?RP
OVERCAST
SE
IO 15
SOUTH
OA 1 i ERY
08/26/91
11/12
SOP
OVFRCAS1
SE
10- 1b
SOUTH
BATTERY
06/26/31
11/ 12
SGP
0VCRCA31
St
10-15
SOUTH
BATTERY
08/26/91
1 1/1'2
SBP
OVERCAST
SE
10- 15
SOU 1H
BATTERY
OR/26/91
1 1/12
SHP
OVFRCAST
SF
10- 1 b
SOUTH
BATTFRY
09/0b/91
1 1/12
SBP
CLEAR
Nf&S
10- 15
SOUTH
BATTFRY
09/C5/9 f
11/12
sap
CI FAR
NF&S
10 15
SOUTH
BAI IFRV
09/05/91
11/12
SBP
CLEAR
NEBS
10- 15
SOUTH
BATTFRY
09/Cb/3 1
11/12
SBP
CI e AK
NFS S
JO 15
SOUTH
BA f Tt-KY
09/00/91
11/12
SBP
CLEAR
NFSS
10- 15
SOUTH
0A1TFRY
09/00/91
11/12
SBP
CLtAR
NESS
10- 15
SOUTH
BATTERY
09/Ui>'9 1
1 1/12
b.HP
CLEAR
NES-S
10 lfi
SOUTH
BATTERY
09/05/91
11/12
SBP
CLEAR
NL&S
10- 1b
SOU 1 H
RATTEHY
09/05/91
11/12
SUP
CLLAR
NLSS
tO 1b
suum
BAITfcRY
C9/Co/'J 1
1 1/12
SUP
CLEAR
NE&S
10- 15
SOUTH
RAT TFRY
O9/09/91
11/12
SBP
CI LAN
SW/SE
t> 20
SOUTH
RAT 1 FRY
09/09/91
11/12
SBP
CL LAW
SW/SE
b 20
SOUTH
BAfffeRY
09/09/9 1
11/12
SBP
CLEAR
SW/SE
5 20
SOU 1H
BATTFRY
09/09/9 I
11/12
SBP
CI PAR
SW/SE
5-20
SOUTH
BATTERY
09/09/91
1 1/' 12
SBP
CLEAR
SW/Sl-
5-20
SOUTH
RATTERY
CUMJLATIVE
tMis^rnN
t I Mr
TIME or
MAX I MUM
CONTROL
OVEN
OF
SOURCE OF
EMISSIONS
OPACITY
SYSTEM
NUMOLR
DAY
EMISSIONS
SFC0ND5
"fa
COMMENTS
SHCNANGO
1 lb 3
11 .1)5
DOON
b9
10
SHLNANUQ
123fe
1 2 : Jfe
DOOR
413
100
SHENANGO
1246
12 : 47
OOOR
58
5
SHtNANGU
1208
13:03
DOOR
37
2 b
SHENANGO
1529
13 07
DOOR
26
80
SHFNANGO
13:32
DOOR
3?
mo
SHENANGO
12 48
13:40
DOOR
65
3f»
KiDr
1 14fi
11:23
DC3GR
-in
AS
KRESS
CHEMICO
1 135
f ! 37
DOOR
57
100
KlOC
I 1 Vi 1
\ ' "iO
DOOR
iC \
5b
Kkl- ^
rm mic.ct
i; '$<»
i ? O ?
DOOR
HI
1\>
CHEMICO
1 1S3
12.13
DOOR
22
15
cntMi ;:n
1240
12 . 34
DOOR
2 7
20
CHEVIC2
1 208
1 ? 4 1
DOOR
29
3D
CHEMICO
1230
12.49
DOOR
45
100
cm mi co
1 24H
12 .
DOOR
1 b
CHEMICO
1 258
13 07
DOOR
27
10
CHkMICO
1 118
1 1 . 27
DOOR
73
55
CHEMICO
1 135
11-53
DOOR
49
6H
CHEMICQ
1 1 b 1
12 02
DOOR
en
20
CHEMICO
1 2 36
12 17
OOOR
1 h
15
CHEMICO
1 153
12 • 10
DOOR
10
5
-------
OBS
22 1
222
223
224
220
22fc
227
228
229
2 30
23 1
232
2 33
734
;>:**>
2 3C
237
238
2'jy
240
24 1
24?
ORS
22 1
222
223
224
22b
2?6
227
220
229
230
•2 A 1
232
233
234
235
230
'J31
238
239
2-10
21 1
242
MjSHFR SIDE OVCN rMJSSlONS OBSH R VA TIDNS lO.fiO Tuesday, March 31, 11
DUPING PUSHING OPERATIONS ONLY
KfitSS DEMONSTRATION PROJECT tfEIHlFHEM SIELL CORI'ORAllON
SPARROWS POINT, MARYLAND
Obbi KVLKt>
WIND
SPt LD.
UBotKVER
DATE
BAKERY
INITIALS
WEATHER
0IUEC1ICM
MPH
LOCATION
BACKGROUND
09/09/9i
11/ 12
SB P
CI EAR
Sw/SE
5-20
SOUTH
H A1TERY
09/09/91
11/12
SUP
CLEAR
SW/SE
5 20
SOU f H
UAf I ERY
09/09/91
1 1/ 12
SGP
CLEAR
SW/SE
5 20
SOUTH
OA ITERY
09/09/91
11/12
SBP
CLEAR
SW/SE
5-20
SOU I H
BAI 1ERY
09/09/91
11/12
SOP
CLEAR
SW/SE
5-20
SOUTH
BAITERY
09/11/91
11/12
S UP
OVIKt'AS1
SW
10 1 L»
SO'J i H
BA11ERY
09/11/91
t 1/ 12
SBP
OVERCAST
SW
IO 15
SOUTH
BATTFRY
09/11/3 J
11/12
SBP
DVERCAS1
SW
10- 15
SOUTH
BAT TFRY
09/11/91
1 i/ 12
SBP
OVERCAST
jW
IO '5
S JUT H
BATTERY
09«' 1 1 / 9 1
11/1?
SUP
OVERCAST
SW
10- 15
south
BATTFRY
09/11/91
1 1/12
SHP
OVERCAST
SW
IO- 15
SOUTH
BA?IERY
09/11/91
I 1/12
SBP
OVERCAST
SW
IO '5
SOUTH
BATTFRY
09/ 11/9'.
11/1?
SAP
OVfRCAST
5W
10- i 5
SOUTH
BATTFRY
09/ 11/91
11/12
SRP
OVFRCAST
SW
10-15
SOUTH
BATTERY
0Ht NANGIJ
SMCNANi'O
SHENANGO
SHENANGO
SHENANGO
SHENANGO
SHENANGO
SHENANGO
bHfcNANGO
SHENANGO
SlfLNANGG
ShLNANGO
1246
1208
123B
124B
1258
! 146
1 135
1 lb 1
12 29
12 36
1 I'jU
1 2-lG
1208
><3fi
1248
1258
1 im
1 135
I lb 1
1236
1153
124
-------
OPS
243
244
245
240
247
24ft
249
250
25 1
252
2b3
254
2bb
256
257
258
253
260
26 f
2b 2
263
261
OQ S
243
244
245
246
247
248
249
250
25 1
252
253
254
255
250
2b/
258
259
26C
261
262
263
264
PLSHLR SIDE OVEN EMIS SIHNS OB Sf" kVA 1 I UNS 10'bO Tuesday, March 31, 1992 12
DURING PUSHING OPF RAT IHNS ONLY
KRESS DEMONSTRATION PROJECT - BETHlFHEM STEEL CORHORATIUN
SPARROWS TOIKT, MARYLAND
OBSERVLk
b
W1NU
SHEtU.
OBSERVEM
DATE
BATTERY
INITIALS
WEATHER
DIRECTION
MHH
IOCATI ON
BACKGROUND
00/23/9 1
1 1/12
SEP
OVERCAS r
SW
ir>-?o
SOUTH
BATTERY
09/23/91
1 1/ 12
SRP
OVERCAST
SW
15-20
SOUTH
BATTERY
09/23/91
11/12
SBP
OVERCAST
sw
15 20
SOUTH
BATTERY
09/23/91
1 1/12
SBP
OVF ROAST
SW
15-20
SOUTH
BATTERY
10/01/91
1 1/12
SEP
OVERCAST
SW
15-20
SOUTH
BATTERY
10/01/91
11/12
SOP
OVERCAST
SW
15-20
SOUTH
BAT I ER<<
10/01/91
1 1/12
SBP
OVERCAST
SW
15-20
SOUTH
BAT I FRY
10/01/91
1 1/12
SBP
OVERCAST
SW
15-20
SOUTH
BATTERY
io/ui/9t
11/12
SBP
OVERCAST
SW
15-20
SOUTH
BAT fLRY
10/01/91
11/12
SBP
OVERCAST
SW
1S -20
SOUTH
BATTERY
10/01/91
11/12
SBP
OVERCAST
SW
15-20
SOU I H
BATTERY
10/04/91
11/12
SBP
CLEAR
NW
0 b
SOUTH
BATTERY
10/04/91
11/12
SBP
CLEAR
NW
0-5
SOUTH
BA1TFRY
10/04/91
11/12
SfciP
CLEAR
NW
0-5
SOUTH
BATTERY
I0/O4/91
11/12
hbP
CLEAR
NW
0-5
SOUTH
BATTERY
10/04/91
11/12
SBP
CI EAR
NW
0-5
SOUTH
BATTERY
10/04/91
1 1/12
SBP
CLEAR
NW
0-5
SOUTH
BATTERY
10/08/91
11/12
SBP
CLEAR
NW
15 20
SOUTH
RATTCRY
10/08/91
1 1 / 12
SBP
CLEAR
NW
15-20
SOUTH
BATTERY
IO/OB/91
11/12
SBP
CLEAR
NW
15-20
SOUTH
BAT 1 EH Y
IO/08/91
11/1?
SBP
CI FAR
NW
15 20
SOU I H
BA1 IfcRY
10/08/91
1 1/12
SBP
CI FAR
NW
15-20
SOUTH
BATTERY
CUMULATIVE
EMISSION
TIME
TIME OF
MAX IMUM
CONTROL
QVLN
Of-
SOURCE Of-
EMISSIONS
OPACITY
SYSTEM
NUMBER
DAY
EMISSIONS
SECONDS
7.
COMMENTS
SHENANGO
1171
12 . 23
OOOR
2 1
90
SHENANGO
1208
12: 37
DOOR
7 1
2b
SHENANGO
1238
12 47
DOOR
01
100
SHFNANGO
1248
12 • 57
DOOR
79
10
K IOC
I 148
t 1 : 18
DOOR
4 1
35
SHENANGO
1222
1 1 : 30
DOOR
ni
50
XT DC
1 151
1 1 : 4fl
DOOR
bO
100
SHENANGO
1 135
12 02
DOOR
70
bb
*IDC
1 1b3
12 22
DUOK
48
100
XI DC
1 1 '19
14 35
ODOR
7?
60
K I DC
1 154
10 10
DOOR
JO
2b
*10C
1 148
1 1 ; 20
OOOR
6 t
35
SHENANGO
1224
11.35
DOOR
6b
40
K I DC
1 1 b 1
1 1 ,4'j
DOOR
•16
20
Sf IflNANiaU
1 1 3b
12 09
DOOP
55
85
HEAVY AT
END
Si tENANGO
1 1 b3
12.17
DOOR
77
15
SHENANGO
1244
12 ; 35
DOOR
54
25
SHENANGO
1 1 34
11:16
DOOR
126
85
KlUC
1 146
1 t ; 47
DOOR
69
90
HEAVY A
tND
SHENANGO
1224
1 1 : 59
DOOR
86
100
SHENANGO
1234
1? :07
DOOR
05
35
KIOC
1 15 1
12: 12
OOOR
42
2b
-------
oas
265
2GG
267
268
269
270
27 1
272
273
2/4
275
2 70
277
278
279
280
281
282
283
234
285
28b
DBS
265
266
267
268
2C9
270
27 \
272
2/3
2 7 1
275
276
277
278
279
280
20 1
282
233
284
285
236
PUSHER SIDE OVEN EMISSIONS O&SCRVATIUNS 10 bO Tuesday. March 31 , 1992 13
DURING PUSHING OPERATIONS ONLY
KRESS DEMONSINA(ION PROJECT - BEIHLfcHtM SIEfcL CORPORATION
SPARROWS POINJ. MARYLAND
WIND
OBSERVERS
WIND
SPEED,
OBSERVER
DA T t
RATTERV
INITIAL S
WEATHER
DIRECTION
MPH
LOCATION
BACKGROUND
10/08/91
11/12
SBP
CLfcAR
NW
lb-20
SOUTH
BA1ItWY
10/08/91
1 1/ 12
SBP
CLEAR
NW
15-20
smiiH
BATTERY
10/08/91
11/12
SBP
CLtAR
NW
15-20
SOUTH
BATTERY
tO/OB/91
11/12
SBP
CLfcAR
NW
15-20
SOUTH
BATTERY
10/08/91
1 1/12
SBP
CLEAR
NW
I h -?o
SOUTH
RA1 1 FRY
10/08/91
11/12
SRP
CI FAR
NW
15-20
SOUTH
BATTERY
10/10/91
11/12
SBP
CLEAR
5W
15-20
SOOT h
BAT TERY
10/10/91
11/12
SBP
CLtAR
sw
1 5 - 20
SOU! H
BA11ERY
10/10/91
1 1/12
SBP
CLEAR
SW
15-20
SOUTH
BAMFRY
U>/ 10/9 1
1 1/12
SBP
C| I AR
sw
15-20
SOUTH
BATTERY
10/10/91
11/12
SBP
CLtAR
sw
15-20
SOUTH
BATTFRY
10/12/91
11
SBP
CLfcAH
NW
10- 15
SOUf H
BATTERY
10/12/91
1 1
SRP
CLEAR
NW
IO- 1 5
SOUTH
RA1 i ERY
10/12/91
1 1
SBP
Ci FAR
NW
10-15
SOUTH
BATTERY
10/12/9 1
t 1
SBP
CI FAR
NW
10- 15
SOUTH
BATTERY
10/12/91
1 1
SBP
CLtAR
NW
10 15
SOUTH
BATTERY
10/12/91
1 1
SBP
CLEAR
NW
10-15
SOU I H
BATTERY
10/12/91
1 1
SBP
CI EAR
NW
10- 1 5
SOU 1 H
BAT 1 CRY
10/12/91
1 1
SRP
CLEAR
NW
10-15
SOUTH
eATTCRY
10/12/91
11
SBP
CLEAR
NW
10 15
SOUTH
BATTERY
10/14/91
1 1/12
SBP
CLEAR
SE
15-20
SOU IN
BAI1ERY
10/14/91
1 1/12
SBP
CLfcAR
SE
15 20
SOUTH
battery
CUMULA IVt
EMISSION
T I ME
TIME OF
MAXIMUM
CUNTHOI
OVLN
01
SUURCfc Ut-
EMISSIONS
OPACITY
SYSTEM
NUMBER
DAY
EMISSIONS
SECONDS
%
COMMUNIS
SHfNANGO
1244
2
IB
DOOR
4 4
2U
SHENANGO
121G
12
34
DOOR
G A
40
KIOC
1 153
2
38
DOOR
56
90
KIOC
1 149
4
32
DOOR
59
25
KIDC
1 152
15
on
DOOR
56
30
K IDC
1 154
15
4 1
DOOR
04
100
KTDC
1 148
1
56
DOOR
33
100
KIDC
1 VjI
12
2 1
DOOR
78
30
KIOC
J 153
12
S J
DOOR
1)9
to
K IDC
1 149
1
09
DOOR
6 I
K)0
K IUC
1 152
14
30
DOOR
4ft
IO
K IDC
i 1 ;6
1
30
OCOR
5 1
100
K IDC
1 1H 1
1 ?
1 1
DOOR
74
m5
K IDC
1 15 3
2
4 5
i>nnw
25
10
K IDC
1 149
4
10
DCOR
n,
tcx>
KIDC
1 152
14
45
DOOR
60
100
K I DC
1 154
15
2 1
DOOR
39
100
KIDC
1147
17
77
OCOR
43
100
KIOC
1135
1?
48
DOOR
bb
100
KIDC
117*.
16
17
DOOR
2 J
u>o
KIDC
i 140
1 1
31
DCOR
78
25
SHENANGO
1224
1
42
ODOR
68
35
-------
00 s
287
288
289
290
291
292
293
294
29'*
290
297
298
299
H(K)
301
302
UO'J
304
30b
306
307
30ft
obS
287
288
289
290
291
292
293
294
295
296
297
296
299
300
301
302
303
30'1
305
306
307
JOB
PUSHLR SIDE OVFN EMISSIONS OfcSStRVAIiDNS 10:b0 luesday, March 31, 1992 14
DURING PUSHING OPERATIONS ONLY
KRESS DEMONSTRATION PROJECT - BETHLfcHtM STtLL CUKHURAI 1 ON
bPAkROwS PQ1N1. MARYLAND
W I NO
OBScRVfcRS
WIND
SPEED.
OBSFRVFR
OATC
CSAI fttfV
INI 1 I ALS
WLAIHtK
DIRECTION
MPH
LOCATION
BACKGROUND
10/14/91
11/12
SRP
CLEAR
S£
15- 20
SOUTH
BAT ILRY
10/14/91
11/12
SBP
CI FAR
SE
1 5 - 5 O
SOUTH
BATTERY
10/14/91
11/12
SBP
CI FAR
SE
15-20
SOUTH
8A1TERY
10/14/91
11/12
SBP
CLEAR
SE
15 20
SOUTH
BATTERY
10/14/9 1
11/12
SBP
CLEAR
SE
15-70
SOUTH
DAITfRY
10/11/91
1 1/12
SRP
CI EAR
SF
15-20
SOUTH
BATTERY
tO/M/91
1 1/12
SRP
CLEAR
SF
15-20
SOUTH
BATTERY
10/14/91
11/12
SBP
CLEAR
SE
15 20
SOU 1 H
BATTERY
10/14/91
11/12
SBP
CLEAR
SOUTH
1 5 - 2 0
SOUTH
BAI1fRY
10/11/91
1 1/12
SKP
CLtAH
SOUTH
15-20
SOUTH
BATTERY
1Of 14/91
11/12
SBP
CLtAW
SOUTH
15-20
SOUTH
BATTERY
10/13/91
1 1/12
SBP
OVERCAST
SF
15-20
SOUTH
BATTERY
10/1//9J
1 1
SBP
RAIN
NORTH
1 h - 2 0
SOUTH
BAT 1LKY
'0/IS/9i
\ i
SBP
CLEAR
NW/SW
15-20
SOUTH
8A1TERY
10/ia/ai
1 1
SBP
CLEAR
NW/SW
15 20
SOUTH
BATTERY
10/ia/9 ?
1 f
SBP
CLEAR
NW/SW
15 -20
SOUTH
•3 A T TERY
10/lfl/9 t
1 1
SBP
CLEAR
NW/SW
15 20
SOUTH
BATTERY
10/18/91
1 1
SRP
C! fcAH
NW/SW
15 20
SOUTH
BATTERY
10/18/01
1 1
SBP
CLFAR
NW/SW
15 20
SOUTH
BAIIERY
10/18/91
1 1
SBP
CLFAR
NW/SW
15 20
SOUTH
BAT 1tWY
10/18/91
1 t
SBP
CLEAR
NW/SW
15 -20
SOUTH
BA|1tHY
10/20/91
1 f
SBP
CLEAR
NORTH
1 b - 2 0
SOUTH
HATTERY
CUMULAT IVL
EMISSION TIME TIME OF MAXIMUM
CONIHUL OVEN Oh SOURCE OF EMISSIONS OPACITY
SYSILM NUMBtR UAY tMISSIONS SECONDS % COMMENTS
KJDC 1151
SHFNANGO 12T14
KIOC 1153
KIOC 1149
KIOC 1152
KIDC 1154
SHHNANGO 1256
KIDC 1149
SHCNANGO 12G1
KIOC 1135
KIOC 117 1
SHENANGO 1153
KIDC 1148
KIDC 1151
KIDC 1153
KIDC 1149
KIDC lift?
KIOC 1 154
KIOC 1135
KIOC 1147
KIDC 1171
Kinc 115 1
12 :03
DOOR
1? • 12
DOOR
12 : 46
DOOR
14:19
DOOR
14:43
OOGR
15:04
DOOR
V) .02
DOOR
17 1G
000 R
17 .28
DOOR
1 / : 3d
UUUrt
17 ;58
DOUR
12:22
DOOR
1 1 : 4 G
DOOR
1 2 ; 02
DOOR
12 :27
DOOR
14 : 18
003R
14 : 48
DOOR
1 6 : ( !
DOOR
17 13
DOOR
17:52
OOOR
1 ft : 1 1
DOOR
1 1 :48
DOOR
71
3(>
82
35
b8
65
54
7 b
64
90
4 7
50
52
20
76
100
6b
75
/1
100
bO
90
49
50
2 1
2h
67
30
74
35
71
20
63
55
7G
100
G5
100
17
100
16
10O
G9
10O
-------
QQS
309
310
31 !
312
313
314
3th
3 1G
317
.118
3 19
320
32 I
377
323
-'24
32'j
32b
327
32B
3? a
330
OBS
309
3 10
31 1
312
113
314
3 1 n
Hfi
317
3 -.a
319
320
32 I
32?
323
1?4
325
3?fi
327
32B
l?3
330
PUSHER SlOt OVEN EMISSIONS OBSERVATIONS 10:50 Tuesday, March 3 1, 1S92 15
DURING PUSHING QPERAllUNb UNLV
KRESS DEMONSTRATION PROJECT - BEIHtEHtM STEEl CORPORATION
SPARROWS P0IN1, MARYLAND
W 1 NO
OBSERVERS
WIND
SPEED.
OBSERVER
GATE
bA1T tKV
INI II ALS
WEATHER
DIRECTION
MPH
LOCATION
BACKGROUND
10/20/91
1 1
SRP
CLEAR
NOHIH
1 b~ 20
SOUTH
BATTTRY
10/20/91
1 1
SBP
CLEAR
NOR 1 H
1b-20
SOUTH
RATTERY
10/20/9 1
1 1
SBP
CLEAR
NORTH
1B-20
SOUTH
BATTERY
10/20/91
1 1
SBP
CI FAR
NORTH
lh-20
SOUTH
BATTERY
J0/2O/91
1 1
SBP
CLEAR
NOW 1H
f5-20
SOUTH
BATTERY
I0/5O/91
1 1
SBP
CLEAR
NORTH
15 20
SOUTH
BATIERY
10/20/91
i l
SBP
CLEAR
NORTH
15-20
SOUTH
BATIfcRY
10/23/91
11/12
SBP
C.« F AM
sw/sr
10- lb
bOUt H
BATTERY
JO/23/91
1 1/12
SBP
CLEAR
SW/SL
10- lb
SOUTH
RATTFRY
10/23/91
11/1?
SBP
CLEAR
Stf/SL
10 15
SOU I H
BAITERY
10/23/SM
11/12
SUP
e i r a a
sw/sc
10 1 5
SUUt H
BAITERY
10/23/!) 1
11/12
SBP
CLEAR
sw/sr
10 - 1 5
SOU 1 H
BATTERY
10/23/91
11/12
SBP
ClCAR
sw/se
10- 15
SUUIH
BATTERY
JO/23/91
11/12
SBP
CI J AW
SV/Sfc
10- lb
SOUTH
RATTFRY
10/23/91
11/12
SBP
CLEAR
SW/Sfc
10- 15
SOUTH
BATTERY
10/23/9 1
1 1/12
SUP
Clear
SW/SE
10- H>
SOU I H
BATTERY
10/23/91
11/1?
SBP
Ci FA(?
sw/st
10 15
SOUTH
BATTERY
10/23/91
1 1/1?
SBP
CLEAR
SOUTH
10 15
SOUTH
BATTERY
10/23/91
11/12
SBP
Ci ear
SOUTH
10 IE
SOU1 i i
HA f IfcWY
10/23/91
11/1?
SBP
CLEAR
SOUTH
10 15
SOU TH
BATTERY
10/23/9 t
ti/1?
SBP
CLEAR
SOOIH
10- lb
SOUTH
BAITERY
10/20/9 1
11/12
SBP
CLEAR
NE
10 15
SOUTH
BATTFRY
CJMULATIVt
EVISS ION
I IMF
TIME OF
MAXIMUM
CUNfROL
UVfcN
OF
SOURCE OF
EMISSIONS
OPACITY
SYSTEM
NUMBER
OAY
EMISSIONS
SECONDS
%
K! DC
1 143
12 1 1
DOOM
73
100
K 1 DC
i is:i
1? 37
DOOR
7U
Gb
KIOC
1 149
14.51
DOOR
89
75
KI DC
1 152
15 15
DOOR
78
35
Kinc
1 154
15.40
DOOR
7 3
100
KIDC
1 135
17 49
DOOR
4 a
1C0
KI DC
1 171
1ft 09
door
2 7
100
ShFNANGO
1 134
1 1 35
DOOM
69
102
K f DC
i 1 4rt
1 1 b?
unoR
6b
25
ShFNANGC
i.»;»4
I l S-i
unoR
L 1
ShFNaNGO
' ?:i4
1? 04
DOOR
ICS
100
Ki JC
11'.) \
12-21
DOOR
7 1
35
KIOC
i 1ST
12 5G
POOR
v \
4 5
KIOC
1 1 -19
14 29
door
84
3 b
SritNANGG
USfi
14 40
DOOR
57
25
SnF NANfif2
* ?68
14 48
DOOR
70
7 0
KIOC
117 2
15 00
DOOR
75
100
KIOC
i 152
1520
DOOR
b3
30
KIOC
1 135
17 15
DOOW
29
55
KIDC
1 154
1? 50
DOOR
3b
3b
K I DC
117 1
18 11
DOOR
57
100
KIDC
1 148
1 1 : bO
DOOR
73
?5
-------
PUSHER SIDE OVEN EMISSIONS OBSERVATIONS 10:50 Tuesday. March 31, 199? 16
DURING PUSHING OPERA 7 IONS ONLY
KRESS DEMONSTRATION PROJECT - BETHLLHFM STEEL CORPORATION
SPARROWS POINT, MARYLAND
WIND
OHSl-RVEMS
WINC
SPFFD.
OBSERVER
06 S
DATE
BATTERY
INITIALS
WfcAIHtW
DIRECT ION
MPH
1OCATION
BACKGROUND
33 1
10/29/31
1 f/ 12
SfcSP
CLEAR
NF
JO- 15
SOUTH
BATTERY
332
10/29/91
1 1/ 12
SBP
CLEAR
NF
10 15
SOUTH
BATTERY
333
10/29/91
f t/ 12
sap
CLEAR
NF
10-
SOUTH
BATTERY
334
10/29/91
11/12
SUP
Ct FAR
NF
10-15
SOUTH
BATTERY
33b
10/29/91
1 1/12
SBP
CLEAR
Nfc
10-15
SOUTH
BATTERY
33«i
10/29/9t
1 1/ 12
SBP
CLEAR
NE
10 15
SOUTH
UAl i tRY
337
10/29/9 f
1 1/12
SBP
CLEAR
NC
10-15
SOUTH
BATIfcKY
33ft
10/29/91
11/12
SBP
CLEAR
NE
lO 15
SOUTH
BATTERY
339
10/29/91
11/12
SBP
CLEAR
NE
10 15
SOU 1H
BAT IERY
340
11/05/91
11/12
SBP
CLLAR
Nfc /NW
15 20
SOUTH
BATTFRY
34 1
1 1/05/3t
1 1 / 1 2
SBP
CLEAR
Nfc/NW
15 20
SOUTH
RATTFRY
342
1 1/05/91
11/12
SBP
clear
NF /NW
15 - 20
SOU IH
RATTFRY
34 3
1 1/05/91
1 1/ 12
SBP
CLEAR
Nk/NW
1 b - 20
SOU 1H
RATTFRY
34-1
1 1/05/91
ii/i2
SHP
CI.* AH
Nt /NW
15-20
SOUTH
BA TTFRY
345
11/05/91
11/12
SBP
CLEAR
NE/NW
15-20
SOUTH
BATTERY
J4fc
i 1 / Ob/91
\ 1/12
SUP
CLEAR
NF/NW
1 !j - 20
SOUTH
BA[TERY
347
11/Ob/91
11/12
SRP
Ct FAR
NE /NW
15-20
SOUTH
U AT 1LRY
348
11/05/91
11/12
SBP
CLEAR
Nt/NW
15-20
SOUTH
BATTERY
349
11/05/91
11/12
SBP
CLEAR
NF/NW
15 20
SOUTH
BATTERY
JbO
11/Ob/91
1 1/12
SBP
CLEAR
NE/NW
15 20
SOUTH
MA 1TERY
351
11/07/91
1 1/ 12
SBP
UVEKCASI
NF
5-10
SOUTH
BATTERY
3b2
t1/0//91
t 1/ 12
SBP
OVERCAST
Nf
5- 10
SOU IH
HA1TERY
CUMUlATIVL
EMISSION
I IML
1IML OF
MAX I MUM
CONTROL
OVEN
OF
SOURCE OF
EMISSIONS
UPACI1Y
OBS
SYSTEM
NUMBER
DAY
EMISSIONS
StCONOS
%
COMMfcNIS
33 1
KIDC
1 ! b 1
12:18
DOOR
GO
30
33?
KIDC
115 3
13 10
noon
18
45
333
KIOC
1 152
14 r 2 1
DOOR
74
100
334
SHENANGO
1228
! 4 :43
DOOR
30
20
335
SHENANGO
1230
14:53
DOOR
22
IOO
330
SHENANGO
1248
15:00
DOOR
G7
15
337
CHENANGO
1258
15 11
DOOR
1b
10
338
shfnango
12t>8
15 : 27
DOOR
75
•15
339
KIDC
1 135
17: 13
»nn«
17
J 00
340
KIOC
1148
11:33
1)001?
G1
70
34 1
SHENANGO
1 P3-I
1 1 - 53
COOR
* 2'
100
342
KIDC
1 15 1
1 1 . 55
DOOR
©b
IOO
34 3
K I DC
t 15 3
1 2 . 30
CODR
89
20
344
Kmc
1 143
14.19
DOOR
12
55
34*.
KIDC
1 J 72
14,41
DOOR
21
IOO
34G
KIDC
1 152
15 .02
DOOR
6-1
30
347
SHENANGO
1201
15.20
OOOR
2t>
15
346
SHENANGO
12 1 1
15.25
DOOM
5
20
349
SHENANGO
122 1
1 b : 32
UOOM
5G
ICO
350
SHENANGO
1231
15 : 39
DOOR
58
60
3*D 1
KIOC
1 146
1 1 . -19
DOOR
34
30
352
KIDC
1 151
12: 11
DOOR
109
25
-------
PUSHf-R SH1F I1VFN FMISSIflNS OBSERVATIONS 10:50 Tuasday. March 31. 1992 17
DURING PUSHING OPERATIONS ONLf
KRESS DEMONSTRATION PROJECT - BETIILCMEM STFFi Ci'.KF-ORA I 1 UN
SPARROWS POINT, MARYLAND
WIND
ORSi-RVFRS
wind
SPEED.
OBSLHVER
OBS
DATE
BATTERY
INITIAL
S WEATHER
DIRECTION
MPH
LOCATION
BACKGROUND
3b 3
11/G//91
1l/t2
SBP
OVERCAST
NF
5 - 10
SOUTH
battery
354
1 1/07/91
1 1/12
SBP
OVFRCAST
NE
5-10
SOU I H
BAITERY
3bb
1 1/07/91
11/12
sap
OVERCAST
f.f
S- 10
SOUTH
BAT 1ERY
3*6
! 1/07/9 1
1 1/ 12
S8P
OVFRCAST
NE
5 10
SOUTH
BAI T tRY
3b?
11/12/91
1 1/12
S8P
OVERCAST
NW
1 5 20
SOUTH
BATTfcHY
35ft
1 1/ 12/.9 1
11/1?
SBP
OVERCAST
NW
1 b - 20
SOUTH
BATTERY
359
11/12/91
11/12
sbp
OVERCAS1
NW
15-20
SOUTH
BATTFRY
3C0
11/ 12/9 t
11/12
SBP
GVfcRC AS1
NW
1 h-20
SOUTH
BATTERY
36 1
1 1/ 12/9 I
11/12
SOP
OVERCASI
NW
1h-20
SOUTH
BATTERY
362
1 1/12/91
11/12
SBP
OVFRCAST
NW
15-20
SOUTH
BATTERY
363
1 1/12/9 1
I 1/ 12
SBP
OVERCAST
NW
15 20
SOU IH
BAIItNY
3G4
11/12/91
11/12
SOP
OVERCAST
NW
1b-20
SOU TH
BATTFRY
365
11/12/91
11/12
SBP
OVERCAST
NW
15-20
SOUTH
BATTERY
3C>ii
11/12/9 }
11/12
SBP
OVERCAST
NW
15-20
SOUTH
BAI!ERY
367
J 1/12/9 S
11/12
SBP
OVERCAST
NW
15 20
SOUTH
BAT TERY
368
1 !/14/9 1
I 1/ 1?
SRP
CLEAR
NW/SE
5 15
SOUTH
BATTERY
369
1 ' / i 4/91
11/12
SHP
c.i far
NW/SE
5- 15
SOUTH
UhTIfcRY
370
1 1/14/91
11/12
SBP
Ci EAR
NW/Sfc
b- 1b
SOUTH
BATTERY
37 1
1 1/14/9 1
1 1/12
SBP
CLEAR
NW/SE
b - 1 b
SOU I H
UAI1tRY
37 2
11/14/91
11/12
SBH
CLLAR
NW/SE
5- 15
SOUTH
RATTFRY
373
11/14/91
11/12
SBP
CLEAR
NW/SE
b 1S
SOUTH
RATTFRY
374
11/19/91
11/12
SBP
Ct EAR
sw
10- lb
SOUTH
battery
CUMULAIIVE
EMISSION'
TIME
TiMt OF
MAXIMUM
CONTROI
OVEN
or
OOUKCL Of
(.MISSIONS
OPAC IY
OBS
SYSTEM
NUMBER
DAY
EMISSIONS
SECONDS
*
CtlMMtN f S
353
KI DC
1 !53
i 2 : 4 2
DOOR
65
3b
354
KIDC
1 149
! 4 • I 8
DOOR
69
2b
35b
K IDC
1 172
14:47
DOOR
81
100
356
KIDC
1 152
lb : 14
DOOR
4 1
ICO
357
ShENANGti
1J 24
1 1 . 29
i;mjr
19
20
308
KIDC
1 1 18
1 1 . 40
DOUR
51
1 h
359
SHENANGO
1244
1 1 ; 4 2
DOOR
35
65
3fcO
SHI NANtiU
12 It
1 1 bH
DOUR
82
ICO
36 1
ShfcNAN'JO
i:»2«
1 ? : 08
nnnR
127
ICO
362
KIDC
1 151
1? 10
DOOR
6 2
ICO
363
SHFNANGO
12 36
1 'j ? 1
DOOR
9 1
1C0
361
KIDC
1 153
12.47
DOOR
*7
3 b
36b
KIDC
J 149
14:4 1
DOOR
04
100
36 fi
K 1 DC
117?
IS ¦ 01
DOOR
102
100
367
KIDC
1 152
15:20
DOOR
70
20
368
KIDC
1 1 48
1 1 : 30
DOOR
OS
io
3 r,n
k r nr.
1 151
1 1 :43
DOUR
71
1CO
370
KIDC
1 153
12 : 10
DOOR
65
10
•J 11
Kiue
1 14H
1 b : Ob
DOOR
22
15
37 'J
KIDC
1 172
15 30
none
84
1C0
373
KIDC
1 If*?
Ih.hh
DOUR
20
374
KIDC
1 1 h 1
13 : 19
DOOR
92
10
-------
PUSHFR Slllh QVFN FMISSIONS OBSERVATIONS 10 50 Tunnday. March 31, 1902 18
DURING PUSHING OPERATIONS ONLY
KRESS DEMONSTRATION PROuFCT - BETHLEHEM STEEL CORPORATION
SPARROWS POINT. MARYLAND
WIND
OBSCRVCRS
MIND
SPEED.
OBSfcRVtR
OB 5
DA IF
BATTERY
INITIALS
WEATHER
DIRECTION
mph
LOCATION
BACKGROUND
375
1 1/19/91
11/12
SliH
CLEAN
SW
10- i'j
SOUTH
BA1IfrRY
376
1 1/19/91
11/12
SB P
CLEAR
sw
10 15
SOUTH
BATTFRY
377
1 1/19/91
1 1/12
SBP
CLEAR
sw
10- 15
SOUTH
BATTERY
378
11/19/91
11/1?
SBP
CI EAR
sw
10- 15
SOUTH
BATTERY
379
11/19/91
11/12
SRP
CLEAR
sw
10-15
SOUTH
BAflERY
330
11/19/91
1 1/12
SBP
CLEAR
sw
in-15
SOUTH
BATTERY
38 1
I 1/19/91
11/12
SBP
CLEAR
sw
'015
SOUTH
BATTERY
382
t 1/21/91
11/12
SBP
OVERCAST
sw
15 20
SOUTH
BATTERY
383
t1/2 1/91
11/12
SBP
OVERCAST
sw
15-20
SOUTH
BATTERY
384
1 1/21/91
11/12
SBP
OVIRCAS I
SW/SE
5-20
S0U1 H
BA1IERY
385
1 1/21/91
11/12
SBP
OVERCAST
SW/St
5-20
SOUIH
fciAl 1 fc HY
3U6
11/21/91
11/12
SCP
OVERCAST
sw/St
\j 20
SOU 1 h
BA1 It MY
387
1 1/21/91
11/12
SBP
OVERCAST
SWSF
5 20
SOUTH
RATTFRY
jda
11/21/91
11/12
SBP
OVtKCASi
SW/St
5 20
SOUTH
BATTERY
389
11/21/91
11/12
SBP
OVERCAST
SW/SF
5-20
SOUTH
BATTERY
3^0
t1/?1/9 1
11/1?
SBP
HVFRCAST
SW
15 20
SOUTH
DATTERY
391
1 1/2 1/91
1 1/12
SBP
OVERCAST
sw
t5 20
South
OA I IERY
392
11/21/31
11/12
SliP
UVLRCAS!
sw
15-20
SOU 1 H
RA11ERY
393
1 1/21/91
1 1/12
SKP
OVbHCASI
SW/SF
5-20
SOUTH
BATTERY
394
11/2 1/91
11/1?
SBP
flVFRCASI
SW/SE
5-20
SOUIH
battcry
39h
11/?1/91
11/12
SBP
OVfcRCAST
SW/SE
5 20
SOUTH
BATTERY
396
1 1/23/91
11/12
SBP
CI FAR
St
10-15
SOUIH
BA11ERY
CLMljl A rIVE
EMISSION
TIME
TIME OF
MAXIMUM
CONTROL
OVEN
OF
SOURCE OF
EMISSIONS
oPACiry
OQS
SYSTEM
NUMBER
day
EMISSIONS
SECONDS
t
COMMENTS
37b
k i do
11 b 3
13 . 36
DOOR
73
20
376
KI DC
1 149
1 'j. on
DOOR
7D
1<>
377
KI DC
1 172
14:21
DOOR
69
100
378
K 1 DC
1 1 52
14 : 36
DOOR
6H
2 5
379
K IDC
1 135
14 : 58
DOOR
26
100
330
KI DC
1 154
15 ; 15
OUUR
15
331
K1 DC
117 1
15 : 34
DOOR
67
ion
382
SHENANGO
I23G
12:34
DOOR
49
30
383
SMFNANGO
1246
1? • 46
DOOft
C, 1
2 5
384
K IDC
1 1 48
12:53
OCOR
78
20
:mri
K R)<
1 1 S 1
13. lb
DOOR
63
30
3B0
K IDC
1 1 5 J
13 3 I
DOOR
y •;>
* 5
39 7
K IDC
1 1 1.4
rj.ii J
DCOR
79
100
jau
K IUC
1172
14.11
DCOR
30
K)0
389
K10C
1 152
14 27
DOOR
63
fiO
390
SHENANGO
12 38
14 54
DOOR
23
45
39 )
SHFNANGO
1
is o;
DDDR
34
100
3q?
SHFNANGO
1
1 h • 1 -j
DOOR
82
70
393
KI DC
1 135
15:53
DOOR
32
100
334
K I DC
1 1 54
16 2-1
DOOR
5
10
3D5
KIDC
117 1
1C 43
DDOR
G5
100
39b
K 1 DC
114a
13:36
DOOR
69
25
-------
OBS
30/
393
399
400
401
402
403
404
405
406
407
4oa
409
4 1<)
-1 1 I
4 12
4 13
4 1
CJKS
397
39ft
399
400
'101
402
403
404
405
406
407
¦103
4 0«1
4 10
4 1 \
4 1 J
4 13
4 4
PUSHER SIDE OVEN EMISSIONS OBSERVATIONS 10:50 luesday, March 31. 13t^ ia
DURING PUSHING OPERATIONS ONI V
KKtS'o DEMONSTRATION PROJECT - BETHLEHEM STEEL CORPORATION
SPARROWS POINT, MARY I AND
WIND
QBStRVIRS
WINO
SPEED,
OBSERVER
OATT
P,A fTFRY
INTTT Ai S
WtAlHfrK
13 L RECTI ON
MP).
iOCATION
BACKGROUND
1 1/23/91
1 1/12
hBP
CLLAK
bt
\Q 15
SOU 1 H
BATTER*
1 l/23/<*I
n/1?
SRP
CLEAR
SE
10- 15
SOUTH
BATTERY
11/23/91
11/12
SEP
CLEAR
SE
10- 15
SOUTH
BATTERY
1 1/23/91
11/12
St3P
CLtAK
St
10 1'-
SOUTH
BA1TERY
1 1/23/91
1 1/12
SRP
CA FAR
SF
10- IB
sdujh
BA1fERY
11/23/9 1
1 1/12
SBP
CI f-AR
SE
10- 15
SOUTH
BATTERY
1 1/23/3 1
1 1/12
SEP
CLCAR
SE
10 15
SOUTH
HA 1 IfcRY
1 1/25/91
1 1/12
SEP
CLEAR
NW
1 h - 20
SOUTH
BATTERY
1 1/25/91
11/1?
SBP
Cut AR
NW
15 20
SOOTH
BATTFRY
1 1/55/91
W 1 2
SBP
C L £ A K
NW
15 20
sauiM
BA1IfcHY
1 1/25/91
1 1/ 12
SBP
CI FAR
NW
IS 20
SOUTH
BATIfcRY
i i/2t>/y 1
1 1/ 12
SBP
Clear
NW
1(5- 15
SUUIH
UA1TERY
1 1/76/91
11/12
SBP
CLEAR
NW
10- 15
SOUTH
HA ITERY
1 i/2fc/y1
11/12
SBP
Clear
NW
10- Ih
SOUTH
battery
11/26/9 1
1 ' / 1 2
SBP
CwEAR
NW
IC- 15
SOU 1 H
BA1IfrRY
11/26/91
1 1/12
SBP
C.I FA«
NW
10- 15
SOtJTl 1
battery
11/26/91
11/12
SBP
CLEAR
NW
10 15
50U1H
BATTERY
I 1/26/91
1 1 / 1 ?
SBP
Ct A W
NW
10 15
SOUTH
BAT|ERV
CUMUIATIVE
EMISSION I I ME TIME Of MAxIMuM
CONTROL OVEN OF SOURCT flF EMISSIONS OPACITY
SYSTEM NUMBER DAY EMISSIONS SECONDS % COMMENTS
K I DC
1 151
13 57
DOOR
75
20
KI DC
1 153
14 13
DOOR
BO
35
K IPO
1 149
14 32
DOOR
90
15
KIDC
1 172
14 5 1
DOOR
10
100
K IDC
1 152
15 1G
DOOR
85
20
KIDC
1 135
15:41
DOOR
39
100
KIDC
1 154
1 5 : 58
DOOR
85
100
K 3 DC
117 1
KIDC
1 152
14 .38
DOOR
5B
100
K IDC
1 135
1 o : 12
DOOR
3B
•K)
KIDC
1 154
15 tO
DOOR
22
20
KIDC
1 148
12 47
DOOR
100
k inc.
1 1b 1
1 2 02
DOOR
oo
100
KIDC
1 153
13 13
DOOR
RC>
25
KIL1C
1 1 VJ
13:26
DOOR
66
7 0
KIOC
H"'/
i A 3 7
DUUW
o2
100
KIDC
1 1 52
13 48
OOOR
64
UK)
KIDC
1 154
14 . (K>
DOOR
74
100
100 DARK
-------
Section 5
Topside Emission Observation Conventional & KIDC - Database
B-39
-------
oii
1
2
3
4
5
0
7
3
9
10
1 1
12
13
M
l«i
i a
S 7
18
19
20
? 1
22
BS
1
2
3
4
5
6
7
8
9
10
i 1
1 2
1 J
•, 4
1 ^
i o
1 /
ia
IrJ
20
2 t
COKE OVFN TOPSIDE EMISSIONS OBSERVA T i ONS
K10C DEMONSTRATION PROJECT - BETHLEHEM SILLL CORPORATION
SPARROWS PU1NI . MARYlANiJ
10:53 Tuesday. March 31, 1992 1
OATE
0:1/19/91
03/19/91
03/19/91
OJ/19/91
03/ 19/91
03/19/91
03/19/91
03/19/91
03/27/9 1
:>3/?7/9 1
03/27/91
03/27/91
03/27/01
03/2H/H
:>:*/ ??)/*) 1
03/25/31
03/20/01
03/20/9 1
04/02/91
04/05/91
04/OS/01
04/05/91
CHARGING
1 1ft 12
1 IS 12
11ft 12
MS 12
1 18-12
1 IS 12
1 \& 12
1 1ft 1 ?
1 IS 12
MAI?
MS 12
MS 12
IIS 12
1 IS 12
1 t A 1 2
J 16 12
US 12
I IS 12
1 IS 12
I IS 12
1 1M2
1 1S12
OBSERVERS
IMTIAIS
CR
CR
CH
CH
CR
CH
CM
CR
sap
SBP
SKP
SHP
SBP
SRP
SBP
SBP
SBP
SBP
SBP
FRC
FRC
FRC
WFATHFR
P f L CLOY
PTL CLOY
P1L CLOY
PTI
PTL
CI DY
CI f) Y
PTL CLOY
PTL CLOY
PTI f.l DY
OVFRC.AS I
nVFRC.A^I
0VFRCAST
HVFHC* AST
GVFRfAST
RAIN
RAIN
RAIN
RA IN
RA IN
fl E AR
DC,RAIN
DC,RAIN
OC,RAIN
WINO
DIRECTION
Wf-Sf
WF ST
WEST
WFST
WFST
WEST
WEST
WEST
SE
SI
SE
SE
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COKE OVFN TOPS IDF FMISSIHNS ORSFRVATIONS 10.53 Tuesday. March 31, 1992
KIDC DEMONSTRATION PROJECT - BUHLEHEM STEEL CORPORATION
bPAKRQWS POINT. MARYLAND
PUSHING
WIND rMTSSJON
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WIND
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CONTROL
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04/25/91
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CUKE CVEN TOPSIDE EMISSIONS CU3LKVA 1 1GNS
KIDC DEMONSTRATION PROJECT - SfclHthHFM SlfcH CORPORATION
SPARROWS H01NT, MARYLAND
10.53 Tuut.day. March 31, 199? 4
PUSHING
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DATE
battery
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05/07/31
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05/07/91
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Oh/07/9 1
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05/07/91
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05/07/H1
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05/07/91
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05/ 14/31
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05/14/01
1 1812
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12-18
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Ob/ 14/91
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05/ 14/91
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05/ 14/91
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05/22/9 1
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0 I
92
93
94
9b
96
97
98
99
100
101
tOi
103
1o4
I C-c
106
107
ioe
100
1 io
OBO
B9
no
9 1
92
93
94
9 b
96
97
98
99
100
10 I
102
103
to.i
105
106
107
108
109
1 10
CDKfc OVt-N I UPSIDE EMISSIONS OBSfcRVAT IONS
KlOC DEMONSTRATION PROJECT BCTIILCHCM STCCL CORPORATION
SPARROWS POINT, MARYLAND
10.53 Tuesday. March 31 , I9y2
DA IE
05/29/
05/29/9
0:i/2 1
1 t& 12
SRP
CI FAR
SF
IS 20
south
BATTERY
SHENANG
M
1 1&12
SBP
CLEAR
5E
15 20
SOUTH
BATTERY
SHENANG
» 1
1 1A 1 ?
SRP
CI 1 AH
SF
1 5 - 'JO
SOU 1 > i
BA 1 IfcRY
SHENANG
~ 1
1 1ft 1 7
SBP
CLEAR
Sfc
1 b - 20
SOUTH
RATTCRY
SHENANG
11
11&12
SBP
CLEAR
SE
15-20
SOUTH
BAUfcRY
SHENANG
1 1
1 1& ! 2
SBP
CLEAR
St
ib 20
SOU 1 H
HA t I Lk'Y
SHENANG
M
1 1&, 2
SOP
CI TAR
SE
15-20
SOUTH
BAT ItRY
SHENANG
M
1 1& i 2
SRP
CLEAR
SE
1b 20
SUUIH
BAHERY
SHENANG
11
11 &' 2
SHP
CLt AR
SE
lb-20
SOUTH
BATTFRY
SHFNANG
M
1 1 & 41!
SBP
01 FAR
SF
15-20
SOUTH
BATTERY
SHENANG
I !
1 1&-.2
SBP
CI FAR
NF
15-20
SOUTH
BAT TERY
SHENANG
I *
1 1 & i 2
SIS-1
CLEAR
NE
15 20
SOU IH
BA11 fcRY
SHENANG
I 4
1 IS i 2
$0°
CLEAR
NE
15-20
SOU I H
KA1ItRY
SHFNANG
I 1
1 1&12
bU-»
CLEAR
Nt
lb 20
SOUTH
BATTERY
SHENANG
1 •
1 1&12
s&»
CLEAR
NE
15 20
SOUTH
BATTERY
SHENANG
~ 1
1 1S 12
SB*1
CLEAR
NE
15-20
SOUTH
RAT TERY
SHFNANG
~ 1
1 IS 1 2
SDP
CLCAR
NE
1b 20
SOU 1 H
BATTERY
SHFNANG
10
CUM.
TIMf
OHO
C-HG
run
CHG
s r AND
T I
ME OF
MAXIMUM
OVFN
OF
HOI F
HOLE
HOLE
HULL
PIPt
EMI
SSIONS
OPACITY.
number
PUSH
ft 1
//2
*3
ffA
CAP
St
CONOS
%
1235
13: 12
10
15
10
1b
3b
ao
35
1245
13 : 20
20
15
5
30
2 b
4 b
30
12bb
1 3 : 3-1
2 b
15
5
25
50
95
50
1 1 27
1 3 : b9
1 b
50
30
25
15
50
50
1 14 7
14 ; O*
70
65
ao
40
30
70
90
1 127
14.41
10
5
20
30
30
70
30
1 147
14 : b2
80
KO
HO
HO
40
CO
ao
1 107
15 :C6
25
50
70
00
50
80
90
1207
15 21
10
5
10
10
25
3b
2 b
• 217
15: 3C
70
70
75
80
ioo
50
100
r.>37
15-3/
' oo
60
40
30
70
70
100
12'*. 7
15: 48
10
5
10
10
40
10
1267
15 : 50
to
10
10
10
4 b
7 b
lb
1209
10 : 13
30
5
10
lb
6b
SO
65
1229
16 : 22
15
10
10
b
'Ah
7h
3b
113b
1 1 : 10
-.oo
70
80
BO
\oo
35
100
1 153
12 : 06
15
5
h
1 h
40
40
40
1233
12:42
15
10
5
5
35
50
35
1243
1? 53
5
10
5
'Q
2 b
4 b
2 b
12G3
13 .06
20
30
10
25
45
95
45
1205
1 3 ; 19
20
70
bO
tiO
100
480
100
12 lb
13:42
30
70
B5
100
•T5
DO
100
-------
OBS
i 1 1
1 12
1 13
1 14
1 1b
1 16
1 17
1 18
1 19
120
12 1
I 22
12 :i
124
' 25
'26
¦. ? 7
128
123
13U
13'
132
OBS
t 11
1 12
1 11
1 14
1 lb
t 16
1 1?
1 18
¦ trt
120
• 2 i
' 2?
1 2 J
12 I
*25
126
127
123
1 29
130
131
'32
COKE OVFN TnPSlOE EMISSIONS OBSERVATIONS
K10(1 OtMONSTRATIDN PROJECT - SETHI EHFM STEEL CORPORATION
SPARROWS POINT. MARVI AND
10:53 Tuesday, March 31, 1992 fc
DA lb
06/04/0 I
06/04/91
06/04/91
Oti/l'J/91
06/13/91
06/13/91
06/13/91
06/13/91
06/13/91
06/13/91
06/ 13/91
06/ 13/91
06/ 13/9 I
06/ 18/9 t
06/ 18 ''91
06/18/9 1
Of/ 16/01
Of. / 18/9 1
06/18/91
0 ~"/ 16/31
06/16/51
06/ 18/91
CHARGING
HOLf
LIDS
OFF
WIND
EMISSION
OBSERVERS
WTNO
SPEED
OPSfrRV* R
CONTROL
BA TTFRV
TMT I A1
s
Wfc A THF R
0TRFC7I0N
MPH
LOCATION
BACKGROUND
SYSTEM
i 1& 1?
SRP
CLEAR
Ni
11.-20
SOUTH
BA 1 l*-RY
SHENANG
11412
SOP
CLCAR
NE
15-20
SOUTH
KAIfhRY
SHFNANG
I 15 12
SBP
CLEAR
NE
15 20
SOUTH
RATTFRY
SHENANG
1 1*12
Rb A
CLEAR
NF
20
TOPSIDE
CLEAR
SHFNANG
1 1& 12
RfcA
Ci FAR
NE
20
TOPSIDE
CI TAR
SHENANG
1 1& 12
Rb A
CA FAR
NE
20
TOPSIDE
CLCAR
SHLNANG
1 1&12
RF A
CLEAR
NC
20
I CPSIDE
CLEAR
SHENANG
11&12
RCA
CLEAR
NE
20
TOPSIDE
CLEAR
SHENANG
t IK 12
RfA
CA FAR
WE
20
TOPSIDE
CLCAR
SHENANG
11X12
RF A
r.i far
Nb
20
TOPSIDE
CLCAR
SHENANG
1 1 & 1 2
REA
CI b AR
NE
20
TCPSIDE
CLEAR
SHENANG
1 tS 12
RCA
CI FAR
NC
'20
UPSIDb
CI EAR
SHINANG
11/1?
REA
CLEAR
NC
20
TOPS IDC
CI EAR
SHENANG
11/12
5 HP
a a i n
E A'j I
13 1U
SOUTH
~ ATI CRY
SHENANG
11/12
SRP
HA IN
fr AST
13- IB
SwU 1 H
BATTFRY
SHENANG
I 1/ 12
sen
RAIN
FAST
13 ia
SOU I H
BA1IbRY
SHENANG
11/ 12
GOP
RAIN
CAST
13 1ti
SCUJH
BAT TFRY
SHFNANG
11/12
SBP
RAIN
EASI
13 18
south
RATI f-UY
SHFNANG
11/1 2
SRP
RAIN
EAST
13- 18
SOU I M
BATTFRY
SHENANG
11/12
OOP
KA IN
EAS 1
13 - 1B
S0U1H
BATTFRY
SHENANG
11/12
sep
RAIN
FAST
13- f«
SOU IN
HA II FRY
SHENANG
1 1/ 12
SBP
RAIN
FAST
13 - 1A
SCJTH
BA If ERV
SHENANG
CUM.
TIME
CHG
t-HG
CMC
CI IG
STAND-
TIME OF
MAXIMUM
OVEN
OF
HOLE
HOLb
HOI t"
HOLb
PIPE
I MISSIONS
OPACITY.
NUMOCR
PUSH
tt 1
a2
*3
VA
CAP
SECONDS
%
1225
13
5a
100
65
65
as
65
80
100
1235
14
. 10
80
100
100
100
8 b
7 b
10C
1245
1 4
20
5
5
10
5
1 5
BO
lb
127 1
1 1
.30
7C
20
1 13b
1 1
4'J
1 10
15
1 153
1 1
75
b
12 13
12
: 13
119
25
1223
12
45
i 22
30
I2'j3
11>
bb
' 18
35
12 A J
13
L)<1
8?
10
• J
i j
\ I
iSf,
55
12 15
1 3
•H:
12 1
20
12 2b
14
07
T 12
15
I2b8
1 1
18
b
10
5
10
20
GO
20
i2fc«
1 1
3R
S
5
15
10
40
75
10
1255
12
00
b
0
0
2C
10
45
20
1 1 35
12
¦J \
JO
30
bO
70
3b
75
70
1 lb'J
12
40
1b
10
30
10
10
40
30
1201
12
57
5
5
lb
0
0
25
1b
12 1 1
13
30
b
1 5
15
20
0
40
20
122 1
13
3y
10
lb
10
10
20
fl5
20
1231
14
00
b
b
10
70
3<>
50
70
-------
noo
13:*
134
135
136
137
138
139
140
14 1
142
143
144
145
146
14 /
1.1b
>49
ISO
101
152
103
154
OBS
133
134
135
136
137
138
130
140
14 I
142
1 lis
14 4
I4i
! 4ti
1 4 '
148
My
1 bO
1b I
152
153
154
COKE OVEN TOPSIDE EMISSIONS OBSERVATIONS
KIUC OfcMUNS THAT I ON PROUfcCT UL r HLCHLM STECL COtfPUrtAfiON
SI'ARRUWS PO INI, MARi'lANH
10.53 Tuesday. Marcn 31. 1992 7
DAT L
OB/ !«/»1
07/02/91
07/02/91
07/02/91
07/02/91
07/02/9 1
QV/02/9 1
07/02/91
0//02/91
07/Q2/9 i
07/02/91
07/05/91
07/09/01
C7/03/9 1
C7/09/31
Of/OH/91
Of/US/91
07/09/9 1
07/09/91
07/09/91
07/09/91
07/ 18/9 1
CHARGING
1/ 12
1/12
1/12
1/1?
1/12
1/12
1/ 12
1/ 12
1/ 12
i/ IP
1/ 12
1/12
1/12
1/12
1/ 12
1/12
1/12
1/ 12
1/12
1/12
1/12
1/12
OQSLKVLKb
INITIALS
SB P
SRP
SRP
SRP
SBP
SBP
SBP
SBP
SBP
C.RP
SRP
SEN-
SOR
SBP
SBP
SBP
SBP
SBP
SBP
SBP
SBP
SRP
WtA THfcR
RAIN
OVERCAST
OVERCASI
OVERCAST
OVERCAST
OVERCAST
OVtRCAST
OVtRCASI
OVERCAST
OVERCAST
OVERCAST
<_LtA4
CLEAR
CLEAR
CLLAR
CLEAR
CI CAR
€L b AR
CLEAR
CLEAR
CI FA/3
CLEAR
WIND
DIRECTION
FAST
SE
St
St
SE
SL
SE
SE
SE
sr
SE
Nu
NW
NW
N*
NW
NW
NW
NW
NW
SW
WIND
SPEED
MPH
13 16
10 15
10 15
10- 1ft
10- 15
10- lb
10 15
10- 15
10 15
10- 10
10- 15
1 b - 20
lh-20
1 b - 20
15 20
13-20
15-20
1b 20
15 20
15-20
1S 2D
10 15
OBSERVER
I DCAT ION BACKGROUND
SOUTH
SOwTH
SOUTH
SOUTH
SOUTH
SUUIH
SOti 1 H
SOUTH
SOUTH
SOU 1 H
SOulH
SOwTH
SOi.TH
SUUIH
SOU I H
SOUTH
SOwTH
S0U1 H
SOUTH
SOUTH
SOUTH
SOUTH
KA I It R¥
BA M fc HY
BAITERY
BATTERY
BATTERY
BATTFRY
BAI IF RY
BATTERY
BAT IfcRV
BAT 11 RY
BATTERY
BATTERY
BATTERY
BATTERY
BATTFRY
BATTfRY
BATItkY
BATTFRY
RATIERY
BATTERY
OAT|fcRY
BAT IEKV
MOLfe
T J ML
CHG
CHG
CHG
CHG
SIANU-
lIMt OF
MAXIMUM
I 105
Ov/FN
OF
HOLE
HOLE
HOLE
HOLE
PIPE
fMlSSIONS.
OPACITY
UFF
NUMBER
PUSH
ft\
f 2
*3
#4
CAP
SECONDS
%
124 1
1 4 : 20
00
15
1 5
GO
50
70
60
ALL
1231
14 : 39
0
0
Bb
8b
8 b
70
£5
ALL
1241
15 01
15
1b
1 b
1b
20
15
ALL
1251
15 . 10
4b
45
45
45
45
35
45
ALL
126 1
15-17
70
70
70
70
65
70
At I
1271
15.22
100
100
100
too
bO
100
ALL
1 125
15:52
100
100
100
too
too
55
100
ALL
1 154
1<0 . 1 1
100
100
too
IOO
IOO
75
100
ALL
MG.'
16 : 20
20
20
:>o
r'O
::o
25
20
Al L
'213
1G 35
35
35
35
35
35
3 b
35
Al L
1223
16 1 1
2 h
25
25
25
25
:k>
25
J
1 135
1 1 35
€5
05
C5
65
fc b
o
' 153
1146
20
15
20
J
1226
12 : lO
too
too
100
100
170
100
J
1 2 36
12 46
as
05
G5
00
1 10
85
3
1246
12 54
15
15
'15
0
20
15
2
12C8
13 13
0
5
10
b
1
12 28
13 27
ic
75
fcO
7 5
3
1 238
13 43
45
45
45
15
40
4b
1
1 2 48
13 : 52
40
40
40
30
40
AL<_
1258
14 02
100
100
100
IOO
100
50
IOO
Al i
1 15 1
1 1 . 22
25
2b
2b
2b
2 b
45
25
PUSHING
EMISSION
CONTROL
SYSTEM
SHtNANG
SHtNANG
SHFNANG
SHENANG
SHENANG
SHENANG
SHENANG
SHENANG
SHtNANG
SHFNANG
SHFNANG
SHFNANG
SHENANG
SHENANG
SHENANG
SHtNANG
SHtNANG
SHFNANG
SHtNANG
SHENANG
SHtNANG
CHtMICQ
-------
OBS
155
15b
157
1b8
150
ibO
1G 1
162
163
164
165
166
167
1GQ
ioy
170
17 1
17 2
l?3
174
IV b
176
CBS
156
Ib7
iRa
Ib9
160
161
162
10 J
164
165
i««
167
168
109
170
17 1
172
173
17.1
175
176
CUKE GVFN TOPS I OF FMISSIONS OBSERVATIONS 10:53 Tuesday, March 31, 1992 8
KIOC DEMONSTRATION PROJECT - BETHLEHEM STEEL CORPORATION
SPARROWS POINI. MARYLAND
PUSHING
WIND
EMISS10K
OBSERVER
S
WIND
SPtfeU
~KSfrRVfcR
CCMIKOI
DAT t
BA1 T LKY
INI 1i ALS
WbAIHfcK
direction
MPH
IOCATION
E4ACKGRGJNO
SYSTFM
07/ta/oi
1 1/ 1?
SBP
CI TAR
SW
10- 1b
SUU 1 H
BAIIfcRY
CHtMICO
07/ 18/91
11/12
SBP
CI FAR
SW
10-15
SOUTH
BATTERY
CHEMICO
07/18/91
11/12
SBP
CI FAR
SW
10- 15
SGJTH
BAT Tf RY
CHEMICO
07/ 18/91
1 1/ 12
SBP
CI TAR
sw
10 15
SOUTH
BATTERY
CHEMICO
07/ia/s1
1 1/ 1?
SBP
CLEAR
sw
10 15
SOUTH
BAI1 FRY
CHEMICO
07/18/91
1 1/12
SBP
CLEAR
sw
10 1b
SUU IH
BAT 1LRY
CHFMICO
07/18/91
1 1/12
SBP
CI EAR
SW
10- lb
SOU 1H
KAI 1 FRY
CHFMlCO
07/1Q/91
11/12
SBP
CLEAR
sw
10- 15
SOUTH
BATTERY
CHEMICO
07/10/91
11/12
SBP
CI FAR
sw
lO- 15
SOUTH
BAT TERY
CHEMICO
07/?h/91
11/1?
SBP
RAIN
sw
5 10
SOUTH
BA11LRY
SHLNANG
07/25/91
1 1/12
SBP
RAIN
sw
b 10
SUU 1 H
BAIIhRY
SHFNANG
07/25/91
1 1/ 12
SBP
RAIN
sw
5 10
SOU 1H
BAT TERY
SHENANG
07/95/31
1 1/12
SBP
RAIN
sw
b- 10
SUU 1 H
BATTERY
SHFNANG
07/25/31
1 1/12
SBP
RAIN
sw
b - 10
SULJ1 H
RAT I FRY
SHFNANG
U 1 /1 'J / 3 1
1 1/12
SBP
RAIN
sw
b- lO
SOUTH
BATTFRY
SHFNANC
07/PS/9 1
11/12
SBP
RAIN
sw
5 - 10
SOU! H
BAII FRY
5HENANG
07/25/91
11/12
SBP
RAIN
sw
5-10
SOUTH
BATTERY
SHENANG
0'/2ii/5M
11/12
SBP
RAIN
sw
b 10
SOU i H
BATTERY
SHLNANG
07/25/91
11/12
SBP
RAIN
sw
5 10
SOUTH
BATTERY
SHENANG
07/30/»l
1 1/12
Slip
OVERCAST
St
10-15
SOUTH
BAIT FRY
CHFMICG
o / / jo/' y i
11/12
SEP
OVERCAST
SE
10 15
SOUTH
HATT FRV
CHFMICO
07/30/91
I 1/12
SRP
ovfrcast
SE
10- 15
SOUTH
BAT TERY
CHtMiCU
CHARGING
CUM
HOLE
T I ME
ChG
CHG
CHG
CHG
STAND
TIME or
MAXIMUM
LIDS
OVEN
U1
HULL
HULt
HULt
HULt
PIPE
EMISSIONS
OPACITY,
OFF
NUMBER
PUSH
#1
02
*3
*4
CAP
SFCONDS
%
Ai 1
1 rj'j
1
44
30
30
30
3C
30
25
no
ALL
1153
1
54
20
20
20
20
20
20
20
ALL
12 22
12
2 7
25
25
25
25
25
15
2b
ALL
1262
13
16
55
55
55
55
55
75
5b
ALL
1272
13
24
45
45
45
45
45
90
4 b
AI |
124?
13
t>8
35
35
35
35
3 b
20
35
ALL
1214
14
06
80
80
80
80
80
35
fiO
ALI
1224
14
22
15
15
15
1b
1b
25
15
ALL
1 2 34
14
3 1
40
40
40
•10
40
40
40
ALL
1153
1
S5
30
30
30
30
30
25
30
ALL
1 1 b 1
12
32
KX)
ICO
100
100
100
90
100
O
\JJ\)
2
4 1
0
0
0
0
30
4C
30
ALL
1242
12
54
25
25
25
?b
3C
?b
ALL
1202
J
02
20
20
20
20
20
35
20
2
1272
13
1b
1b
lb
i 5
15
45
15
ALL
1 135
rj
34
100
ICO
100
100
100
40
100
At 1
1 166
13
47
fl5
ns
9h
9b
9b
bb
9b
ALL
1214
14
01
15
15
15
15
20
15
ALL
1224
14
07
55
bh
5h
bb
55
30
55
1
M b 1
1
38
20
20
35
20
3
1 13b
1
4h
30
30
10
43
30
0
1 153
12
02
0
0
0
-------
OOKF OVEN I UPS IDL EMISSIONS OBSERVATIONS
KiUL DEMONSI RAT iON PROJECT - BETHLEHEM STFFI CORPORAT I (IN
SPARROWS POINT, MARYlAND
10:b3 Tuesday. March 31. 1992 9
PUSHING
w: no
FMIS5I0N
OBSERVERS
W! NO
SPEED
OBSERVER
CONTROL
ORS
DATF
RAT I FRY
INITIALS
WEATHER
DIRECTION
MPH
LOCATION
BACKGROUND
SYS 1tM
177
07/30/111
11/12
SBP
OVCRCAST
SE
10 lb
SO J 1 H
bAIIERY
CHEMICO
17B
07/30/91
11/12
SBP
OVERCAST
SE
10- If)
SOUTH
BATTERY
CHFMICO
179
07/30/91
1 1/12
SBP
OVERCAST
SE
10- 15
SOUTH
BAITERY
CHEMICO
180
07/30/91
11/12
SRP
OVFRCAST
SE
10 lb
SOUTH
OATTERV
CHEMICO
181
07/30/01
1 1/12
SBP
OVERCAST
SE
10 5
SOU 1 H
BAIItRY
CHEMICO
182
07/30/91
1 1/12
SBP
OVERCASI
SE
10 1b
SUUIM
BATTERY
CHEMICO
IB 3
07/30/9 1
11/12
bbP
OVLRCAST
SE
10- 15
SOUTH
BAI 1i MY
CHEMICO
18*1
OV/31/91
11/12
GW
OVFRCAST
C,F
h- 10
TOPSIDE
Ct CAR
SHENANG
18b
07/31/91
1 1/12
GW
OVERCAST
SE
5- 10
TOPSIDE
CI EAR
SHENANG
186
07/31/3 1
11/1?
GW
OVERCASI
SE
5 10
TOPSIDE
CLEAR
SMENANG
187
07/3 1 /9
11/12
GW
OVCRCAST
SF
5 10
TOPS IDF
CI r AH
SHENANG
163
07/31/91
11/12
GW
OVlKCASI
SE
5 10
lOPSIDt .
CLEAR
SHFNANG
i«h
07/'J «/9 1
11/12
Hi A
OC/CLEAR
SE
10
SOUTH
HAT 11 RY
SHFNANG
190
07/3'. /3 1
11/12
RE A
OC/Cl EAR
SE
1C
SOUTH
BATTERY
SHENANG
in t
07/3 */91
11/12
REA
OC/CLEAR
SF
10
SOUTH
BATTERY
SIlENANU
192
07/3 1/01
11/12
K1IA
OC/Ct EAR
SL
io
SOUTH
CAT UWY
SHENANG
193
07/31/91
11/12
RCA
OC/CLEAR
S£
'0
SOU I H
HA 1 1EHY
SHENANG
194
0 / / J 1 / 0 1
< i/12
SUP
OC/CLEAK
SL
b - 10
SOUTH
BATTFRY
SHFNANG
t95
07/31/91
15/12
SRP
OC/CLEAR
sr
5- 10
SOUTH
RATTFRY
SHENANG
19*
07/31/91
11/12
SBP
OC/CLEAR
SE
5-10
SOUTH
battery
SHENANG
107
07/31/91
11/12
SBH
UC/CLCAR
SE
b 10
SOUTH
BAT TERY
SHENANG
198
C7/31/91
11/12
SBP
OC/Ct EAR
SE
h- 10
SflUTH
BATTERY
SHENANG
CHARGING
CUM
HOI E
T IMF
CHG
CHG
CHG
CHG
SIAND-
TIME
OF MAXIMUM
LIDS
OVEN
OF
HOLE
HOLE
HULL
HOLE
PIPE
EMISSIONS, OPACITY.
OBS
OFF
MUMBfc R
P'.iSH
if 1
P2
03
<*4
CAP
SFCONDS %
177
ALL
12 1
1b
1b
15
1 b
35
15
186
AL I.
12 12
11 18
IE
5
IB
1 5
15
J?
1b
IE7
3
12S2
14-2C
1 h
lb
15
15
27
lb
tea
ALL
12 7 2
1 i JO
1 V
t b
1 b
lb
lb
b&
15
l«9
ALL
122 2
13 3 1
DO
90
GO
DO
90
52
90
190
At t
12 32
13 • hi'
0
If:
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15
15
46
15
19 *
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12-42
14.19
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45
45
4b
4 b
20
4 fj
*92
3
1 282
14
1b
lb
1b
15
22
15
193
ALL
1 272
14 40
20
20
20
20
:»o
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20
194
AL'.
1222
13 3 1
90
90
90
90
90
52
90
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1 232
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16
15
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15
45
15
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20
20
20
20
20
40
20
197
3
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15
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198
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-------
CGKL OVEN TOPSIDE EMISSIONS OBSERVATIONS
K1PC 11F MONSTRAT ION PROJECT - RF1HIFHFM STFFl COI3PORAT I ON
SPARROWS POINT, MARY I AND
10 53 Tuesday, March 31, 1002
PUSHING
WIND
EMISSION
QB^FRVFRS
WINn
SPEED
observlr
control
OBS
DATE
BAl1LRY
INITIALS
WEATHER
DIRECTION
MPH
iocar con
BACKuROUNO
SYSTEM
?:m
08/20/91
11/12
SOP
OVLRCAST
NORTH
i> 10
SOU IH
BATTERY
CHfcMICO
2??
08/20/91
11/12
SBP
OVCRCAST
NORTH
b 10
SOUTH
6A 1 I FRY
CHfcMICO
??3
08/20/01
11/12
SOP
UVLKCAbI
NOKIIi
'.j- io
SO(l IH
EATTERY
CHEMTCO
224
08/20/9 1
11/12
SBP
OVERCAST
N0R1H
b- 10
SOU I H
BATTERY
CHFMICn
225
08/20/91
1 1/12
SBP
OVERCAST
NOR 1H
b- 10
SOU f H
BATTERY
CHFMirn
226
OB/20/9 1
11/12
SBP
OVERCAST
NORTH
5- 10
SOUTH
BAl ff-RY
CHFMTCn
22?
08/20/91
11/12
SBP
OVFRCAST
NOR IH
5-10
SOUTH
BATTERY
CHCMICO
228
06/20/91
11/12
SBP
OVERCAST
NOR 1H
5-10
SOU f H
BATTERY
C\ICMICO
2 29
08/27/91
11/12
SBP
OVfPCAST
SC
5 10
SOUTH
OAIT|KY
CHfcMICO
230
OB/27/9 1
11/12
SBP
OVERCAST
SE
5-10
SOUTH
BA 1 TERY
CHEMTCO
231
08/27/9 1
11/12
SBP
OVFRCASI
SE
3*10
SOUTH
BATTERY
CHEMTCO
2.7 2
Ofl/27/9 1
11/12
'.HP
ovlrcast
SL
b 10
SOU 1 H
BAl1ERY
CHEMTCO
233
08/27/91
11/12
SOP
0VCRCAS1
SE
5 10
SOUTH
BATTERY
CHEMICn
OB/2 7/9 1
11/1?
SEP
OVCRCAST
SE
¦j 10
SOU I H
BAl1t R Y
CHfcMICO
23b
08/27/S 1
11/12
SBP
OVERCAST
St
b-10
SOUfH
BATTERY
CHFMTCO
23G
08/27/SJ
11/12
SfcP
OVhHCAS1
SE
5-10
SOUTH
BATTERY
ChCMICO
2 J 7
08/27/3 \
11/12
SBP
OVFRCAST
SF
5-10
South
BATTERY
CHfcMICO
?33
Ofl/27/91
11/12
SBP
overcast
SE
5- 10
SOUTH
BATTFRY
CHFMTCn
239
09/04/91
1 1/12
SEP
OVERCAST
SOUTH
1b 2 'J
SOUFH
BAl 1 FRY
SHENANG
240
03/04/9 J
11/12
SBP
OVfcRCAS!
soum
15-20
SOUTH
EATTERY
SHENANC
2-1 1
09/04/91
1 1/12
SBP
OVERCAST
SOUTH
15-20
SOUTH
BATTTRY
SHENANG
242
uy/04/y1
1 1/12
SBP
OVERCAST
SOUTH
15-20
SOUTH
BATTERY
ShENANG
CHARGING
CUM.
HfH F
I IMF
C.HG
CHG
C: it CHG
bT AND
I t ME OF
MAXIMUM
LIDS
CVCN
or
MOLE
HOLE
HOLE HOLE
PIPE
EMISSIONS
OPACITY.
OBS
Cf f-
NUMBER
PL
5H
* 1
#2
ft 3 V4
CAP
SECONDS
%
221
A1 1
1 135
12
50
2G
35
22 2
0
1 IbJ
U
0
100
225
Al L
1246
13
40
35
40
226
3
1208
13
54
0
44
80
227
3
1238
14
10
0
49
90
2 28
3
i24a
4
24
0
bJ
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11^1
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4 0
ioo
? 30
At L
1236
12
02
19
100
? J i
61 I
I <03
2
14
2 7
15
232
ALL
1246
12
?a
4 1
35
233
ALL
1 200
12
J3
3d
25
? 14
C
i 2.1 ft
2
•iU
o
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0 CI
0
0
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235
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1 248
12
b 1
0
0
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a
60
? ih
3
1250
13
00
0
37
HO
2J7
AI L
1268
13
07
3ft
10O
238
ALL
120 1
13
30
4 1
10
2 33
ALL
123 2
14
48
15
10
240
A ( I
1 24 1
14
55
10
lb
211
ALL
12b 1
15
07
19
15
? 4 2
At I
1257
ir>
15
14
IO
-------
CUKt OVEN lOPSIUt LM1SS1QNS OBSERVATIONS
KI DC DEMONSTRATION PROJECT - RETHl FHEM STFtl HORPORAT I ON
SPARROWS POINT. MARYLAND
10.53 Tuesday. March 31. 1392 12
WISHING
WiNLJ FMISS10N
ORSFRVf- HS
Wl MD
SPhtU
OBSERVER
CONTRO:
ORS
DATE
BATTERY
INITIALS
WCATHFR
DIRECTION
MPH
LOCA1 IUN
BACKGROUND
SYSTEM
243
09/04/91
11/12
SBP
OVERCAST
SOUTH
1 5-20
SOUTH
BATTERY
SI ILNANG
244
09/04/91
1 1/12
SBP
DVERCAST
SOUTH
lb-20
SOUTH
BATTERY
SHENANG
245
09/04/9 1
11/12
SBP
OVERCAST
SOUTH
15-20
SOUTH
BATTERY
SHCNANG
246
09/04/y1
11/1?
SHP
OVERCAST
SOUTH
15-20
SOU! H
BAT TERY
SMLNANG
247
09/04/91
1 1/12
SBP
UVCRCASI
SOU 1H
1b-20
SOUTH
BAT1ERY
SHENANG
?4fl
09/04/9 1
11/12
SBP
UVLKCAS1
SOUTH
1 b ?0
SOUTH
RATTFRY
SHFNANG
?49
OH/ 10/9 1
11/ 12
SBP
DVCRCAS!
sw
1b-2G
SOUTH
BATTFRY
KIOC
250
09/10/91
1 1/12
SBP
OVERCAS!
sw
1 b~ 20
SOUTH
RATTFRY
SHFNANG
25 1
03/10/91
11/12
SBP
cjwt kcas r
sw
15 20
SOUTH
BATTERY
SI ff NANG
252
09/10/91
11/12
snp
OVfcRCASI
sw
15-20
SOUTH
RATTFRY
KIDC
2h3
09/ 10/9 1
1 1/12
SBP
0VCRCAS1
sw
1b-20
SOU 1 H
BATTFRY
SHENANG
254
01/ 10/91
11/12
SOP
ovlrcasr
sw
lb-?0
SOUTH
RATTFRY
SHFNANG
255
03/10/9 1
11/12
SBP
OVERCAST
sw
15-2C
SOUTH
HAT FFRY
SHENANG
2bG
09/ 10/9 1
11/12
SBP
OVfcRCASl
sw
15 20
som h
RAT TI-RY
SMLNANG
r
oj/ m/g f
f f / 1 2
SBP
OVERCAST
Sw
1S-20
SOUTH
HA I IIRV
SHfcNANG
?:~>a
09/10/9 1
11/12
SBP
OVfcRCASl
sw
15-20
SOUTH
BATTERY
SHFNANG
2 b'J
09/ 16/9 1
11/12
SUP
(JVfc RCASI
SE
15-20
SOUTH
BATTERY
SHENANG
2 GQ
03/»B/y 1
1 1/ 12
SBP
nvFRCAST
SE
15 20
SOUTH
BATTERY
SHENANG
261
09/ IB/9 1
11/12
SRP
OVI- RfA$T
SE
15 20
SOUTH
UAtTERY
SHENANG
262
09/ 18/9 1
1 1/12
SBP
OVERCAST
SE
15-20
SOU f H
BATTERY
SHENANG
263
09/ IB/91
11/12
SBP
OVrRCAST
Sfc
1b-20
SOUTH
BATTERY
SHFNANG
264
09/18/91
11/12
SBP
UVtRLASl
Sf
Vj 20
SOUTH
BATTERY
SHENANG
CHARGING
CUM.
HOLE
time
C.HG
c.hg
CHG CHG
STANO-
TIML Of
MAXIMUM
LIDS
OVEN
OF
HOI F
HOI F
HOI F HOI i
= pr
EMISSIONS
OPACITY.
DBS
UK
NUMBfcR
PUSH
¥ i
#2
*3 ft 4
CAP
SECONDS
%
243
1
120 1
15: 24
0
0
O
0
40
RO
244
ALL
1271
15:32
53
85
?4b
Al 1
1 1 34
1 K: 13
22
35
246
all
1 154
16: 28
34
75
247
all
1213
16: 39
6 1
100
?4A
all
1223
16.48
51
249
all
1 149
1 1 ; 23
61
100
250
all
1 13b
1 1 ; 36
53
100
2b 1
all
123C
1 1 . 46
6b
100
252
ALL
1 1a 1
12 :05
63
55
2?>3
3
1246
12 : 20
0
39
lb
254
Al l.
1 153
12-31
49
45
255
3
12C9
12:43
0
48
100
3
1 23B
13 . Ot>
0
60
100
257
0
1240
13.19
0
0
0 O
o
0
0
250
3
1258
1 3 ;
0
58
IOC
253
ALL
1 i»ljH
in. 13
62
100
260
ALL
126B
13:20
4 1
100
261
ALL
12C f
13: 29
50
/b
262
ALL
12 11
13-38
98
lb
263
ALL
122 1
13: 47
2B
100
i»b4
ALL
123 1
13 . 56
25
10
-------
DBS
2bb
266
'J In'?
268
269
270
71 1
272
2 73
2 7-1
275
276
277
2/8
279
280
2a 1
282
233
284
280
236
OBS
?T>5
266
267
268
269
270
27 1
272
2 v :>
27 4
275
27G
277
278
2/9
280
28 1
282
283
284
28b
286
COKh OVcN lOPSIOf- EMISSIONS OBStRVAIIONS
K I DC UEMGNSTRAIIflN PKOjfeCT - BETHIIHf-M S T I- f- . C0RPGRATI0N
SPARROWS POINT. MARYIANO
10:53 Tuesday, March 31, 1992 13
OBSERVERS
WlNO
WIND
SPLLU
OBSERVER
PUSHING
EMISS ION
CON i KUL
DATE
09/ 18/9 1
03/ 18/9 I
09/ 18/9 1
09/ 18/91
09/24/91
09/24/9 I
09/24/9 I
09/24/9 1
09/24/9 I
03/24/9 1
03/24/91
03/25/9 I
09/25/91
U3/2b/9 1
10/02/9\
10/02/91
10/02/91
10/02/91
10/02/9 1
10/02/9 1
10/02/91
10/02/91
CHARGING
HULL
LIDS
orr
ALL
ALL
ALL
Al 1
AI I
Al L
ALL
A i t
Ai 1
Al l.
Ai t
Ai i
ALL
ALL
Al L
ALL
1
A! I
ai i
J
3
3
liAT TERY
INITIAL
S
WIAIHER
OIRECTION
MPH
LOCATION
BACKGROUND
SYSTFM
11/12
SBP
OVERCAST
SE
'.5-20
SOUTH
BATTERY
SHENANG
1 1/12
SRP
OVERCAST
SE
15 20
SOUTH
BAT!tRY
SHFNANG
11/12
SBP
OVERCAST
St
15-20
SOUTH
BATTERY
SHENANG
11/12
SBP
0VF RCAST
SF
20
SUllTH
BAT rcRy
bHENANG
11/ 12
SRP
OVFRCAST
NF
12- 15
SOUTH
BA1IERY
SHENANG
1 1/12
SBP
OVERCAST
NE
1? 1b
SOUTH
BATTLRY
SHENANG
ll/l?
SBP
OVERCAST
NE
12 1'j
SOUTH
KM I e WY
SHENANG
I 1/ 12
SBP
OVERCAST
NE
12 15
SOUTH
BATTtRY
SHENANG
i i/ 12
SBP
OVERCAST
NE
12 lb
buum
BAT TERY
SHENANG
11/12
SRP
OVERCAST
NE
12- 15
SOUTH
BATTERY
SHENANG
11/1?
SBP
OVFRCAST
Nl
12- 15
SOUTH
BA1TERY
SHENANG
11/12
SBP
WAIN
WIST
1 d-20
SOU f H
BATTERY
SHFNANG
11/1?
SBP
WAIN
wtsi
1 b - 20
south
BATTFRY
SHENANG
11/12
SBP
RAIN
Wt-ST
1 b - 20
SOUTH
BAT TERY
SHENANG
11/12
SBP
OVERCAST
SOUTH
1 b ?0
SOUTH
RAT T FRY
KIDC
11/12
SUP
OVERCAST
SOUTH
15-?0
SOUTH
RATTFRY
CHEM!CO
11/12
SBP
OVERCAST
SOUTH
15-20
SOUTH
BAT f tRY
K IDC
11/1?
SBP
OVFRCAST
SOIIIH
15 - 20
SCUT H
BATTERY
CHEMlCO
11/f2
SBP
OVERCAST
SOUTH
15 20
SOUTH
BATTfcHY
KMC
11/12
SOP
OVERCAST
SOU II!
15 20
SUUIM
BAT ItRY
KIDC
1 1/12
SBP
OVEHCASJ
SOUTH
' b - ?G
SOUTH
BATT FRY
KIDC
1 1/12
SUP
OVERCAST
SOU 1H
1b 20
SOU! H
RATI FRY
KIDC
CUM
I I Ml
CHG
CMC*
CHG CHG
STAND-
TIME OF
MAXIMUM
uvin
Of-
HOLfc
HOLE
HOLE fUJLfc
PI Pf
frMIssIONS
OPACITY,
NUMBER
PUSH
# 1
*2
ft A
CAP
SECONDS
'/
124 1
14 . 03
37
20
1251
14 : 10
24
1b
1255
14 : 32
2 1
10
126 1
14-48
49
100
1 151
11:44
48
75
123S
1 1 : b9
57
100
1 153
12.12
17
15
1246
12:28
29
10
1 17 1
17 37
e 1
100
1 20 8
17-50
22
10
1229
13 01
57
lb
H7I
13 -a*
69
100
1208
13.5?
3 1
1b
1238
13. Si a
4 1
100
1 119
14.1-1
8b
00
1208
1 '1 . 3 1
?6
20
1 1552
14 . 40
0
0
O
ft?
60
1229
14 : 50
23
15
1 1 b4
15:05
70
100
1 101
17:11
0
63
100
1 147
18:14
0
43
100
117 1
18:53
c
72
85
-------
COKC OVLN TOPSIDE EMISSIONS OBSERVATIONS 10:b3 Tuesday, March 31. 1992 14
KI DC Of MONSTRATION PROJCCT - fifTMiEHEM STEEL CORPORATION
SPARROWS POINT, MARYLAND
PUSHING
WIND
EMISSION
ORSFRVFRS
WFNO
SPFFO
OBSERVER
CONTROL
OBS
DAI L
BATTERV
INITIALS
WEATHER
DIRECT!ON
MPH
1OCAT TON
4 AC'KCiKOIJNO
SY st rM
287
10/04/91
11/12
sap
CLEAR
SE
O 5
bUUHi
UA I ItK/
SHENANG
283
10/04/91
1 1/12
5BP
clear
SE
0 5
SOU 1 H
BATTERY
SHENANG
2B9
10/04/91
1 1/ 12
SBP
CLEAR
Sfc
0-5
SOU 1 H
BATTERY
SHENANG
290
lO/OH/3 1
11/12
SOP
CI fc AR
SW
15-20
SOUTH
BAITERY
SHENANG
291
10/09/91
1 1/ 11>
SBP
(It fc AR
sw
15-20
SHUTH
BATTERY
K10C
292
10/09/91
1 1/ 12
SBP
CI FAR
SW
15-20
SOUTH
BAI J LRY
SHENANG
293
10/09/91
1 1/ 12
SRP
CLEAR
SW
15 20
SOUTH
RAT If-Rf
K IDC
294
10/09/91
1 1/ 12
SBP
CLEAR
SW
15 20
SOUTH
BATTERY
SHfcNANG
295
10/ 09/511
1 1/ 12
SBP
CLEAR
SW
15 20
SOUTH
OAT IEKY
SHCNANo
10/09/91
1 1/ 12
SBP
CI FAR
SW
15-20
SOUTH
BAT f LRY
KIOC
297
10/09/91
1 1/ 12
SBP
CLEAR
SW
15-20
SOUTH
BATIERf
SHENANG
298
10/09/91
1 1/ 12
SDH
L'LLAk
SOUIM
1b-2U
S'JUIH
HA 1 1 fc. R Y
KIDC
299
10/09/91
1 1/ 12
SBP
clear
SOUTH
1b-20
SCUTH
BAT 1 FRY
K 1 Of!
J GO
10/09/91
f 1/ 12
SBP
CI fc A R
SOUTH
15 -20
SOUTH
BATTERY
KIDC
30 t
10/09/91
ll/l?
SBP
CI f AR
SOUTH
15 20
SOUTH
DAT 1LRV
K IDC
302
10/09/91
11/12
SBP
CLEAR
SOUTH
15 20
SOUTH
BATTFRY
K J DO
303
10/09/91
1 1/ 12
SOP
CLEAR
SOU III
fb 20
S2UJH
BATTERY
KIUC
304
10/11/91
1 1
SBP
RAIN
NE
0-b
SOUTH
BATTERY
KIDC
JOS
10/11/91
1 1
SBP
RAIN
NE
0-5
SOUTH
BATTERY
Kinc
JOtt
10/11/91
1 1
SBP
RAIN
NF
()-b
SOUTH
BAITFRY
Kino
307
10/11/91
1 f
SBM
RA 1 N
m
O-S
SniJJH
BATTERY
Kinc
308
10/11/91
1 1
SBP
RAIN
NE
0-5
SOUTH
BATTERY
KIDC
CHARGING
CUM.
HOLE
TIME CHG
CHG
CHG CHG
STAND-
TIME OF
MAXIMUM
LIDS
UVEN
Of- HOI t
HQLfc
HOLE HOLE
PIPE
EMISSIONS
OPACITY,
DBS
OFF
NUMBER
PUSH #\
*7
#3 *4
CAP
SFCONftS
%
287
ALL
1216
12:48
44
55
288
AL L
1226
13:09
25
25
289
AI 1
1236
13 20
51
100
200
A 1 1
1 134
i 1 :i i
57
45
291
ALL
1148
1 1 :46
63
8b
292
3
1224
1 1 :55
0
j a
6 b
293
ALL
1151
12.07
7 3
3 b
294
ALL
1234
12 11
4 7
20
295
ALL
1244
12 : 24
28
20
206
ALL
1 153
12.37
01
100
297
ALL
12 16
12 42
3b
100
29B
At. L
1 149
! 4 11
G3
100
299
At L
1 152
IS 00
58
100
JOG
AL I
1 lb 4
lb 2B
6 \
100
301
At I
1 101
17 4?
h'1
70
302
ALL
1 135
18 01
61
100
303
ALL
1 17 1
18 2 1
69
10U
3C4
Al 1
1 148
1 1 sn
329
100
305
ALL
1 151
12:39
70
100
306
Al 1
1 153
13 30
58
90
30''
At t
1 149
14 IB
4 1
10O
3(58
ALL
1 152
lb 2B
230
75
-------
UK b
309
310
311
312
3 13
3 14
31b
3 16
3!?
3 IF.
319
320
32 1
32?
323
3 24
J 2 b
326
32 7
32fi
329
330
DBS
309
3 10
311
312
313
3 14
315
316
317
3 18
3 10
320
32 I
322
323
324
325
U7G
327
328
329
330
CUKfc UVFN TOPSIDE EMISSIONS OBSERVATIONS
KI DC DEMONSTRATION PROJECT - BETHLEHEM STEEL CORPORATION
SPARROWS POINT, MAftYLANO
10:53 Tuosday. Marcn 31, 1902 15
PUSHING
WIND FMISSION
OBSERVERS
WIND
SPEED
OBSERVER
CONTROL
DATE
BATTERY
INITIALS
WEATHER
DIRECTION
MPH
LOCATION
BACKGROUND
SYSTEM
10/11/91
1 1
SKP
RAIN
NC
0-5
SOUTH
BATTERY
K IDC
10/11/91
1 1
SBP
RAIN
NE
O 5
SOUTH
BATTERY
KIDC
10/13/91
1 1
SBP
OVERCAST
NORTH
10 1b
SOUTH
BA1F ERY
KIDC
10/13/91
1 1
SBP
OVERCAST
NORTH
10- 1b
SOUTH
BAIItRY
K IDC
10/13/9 1
1 1
SKP
OVtRCASI
NORTH
1Q 15
SOU 1 H
BATTFRY
K IDC
10/13/91
1 1
SBP
OVERCAST
NORTH
10- 15
SOU 1 H
BAIIERY
KIDC
I0/13/H1
1 1
SBP
OVERCAST
NORTH
10 !5
SOUTH
BATTERY
KIDC
10/13/91
i 1
SBP
OVERCAST
NORTH
10- 15
SOUTH
BAI1tWY
KIDC
10/13/91
1 1
SBP
UVEKCASI
NOR 1H
10- 15
SOUTH
BATTERY
KIDC
10/13/9 J
1 1
SUP
overcast
NORTH
10 15
SOUTH
BATT ERY
KIDC
10/13/91
1 1
SBP
OVCRCAST
NORTH
10-15
SOUTH
BATIERY
KIDC
10/15/91
11/12
SBP
OC/RAIN
SL
15-20
SOUTH
BATTERY
SHENANG
10/15/91
11/12
SBP
OC/RAIN
SE
lb 20
SOU I H
BATTERY
SHENANG
ir>/1 ®s/91
11/12
SBP
OC/RAIN
SE
15 20
SOUTH
BATTERY
SHENANG
10/15/9 1
1 1/12
SBP
OC/RAIN
SE
15-20
SOUTH
BATTERY
SHENANG
10/ 15/01
t 1/12
SRP
UC/KAiN
St
10 20
iUUlM
BA1T LRY
SHENANG
10/19/91
1 1
SBP
CLEAR/OC
SW/NW
b - 20
SOU 1 H
HA IIfcRY
Kinc
10/19/91
1 1
SbP
CLEAR/UC
SW/NW
b 20
SOU \ H
RATTFRY
KIDC
10/19/31
1 1
SBP
CLEAR/OC
SW/NW
5-20
SOU 1H
BATTERY
KIDC
10/19/31
1 1
SBP
CLEAR/OC
SW/NW
5-20
SOUTH
BATTERy
KIDC
10/19/9 1
1 1
SBP
CLEAR/OC
SW/NW
5-20
SOUTH
CATTERY
KIDC
10/19/91
1 1
SbP
CLEAR/OC
SW/NW
5 20
SOU I H
BATTERY
KIDC
CHARGING
HOL E
I IDS
OFF
ALu
Al 1
ALL
ALL
ALL
Al I
ALL
ALL
ALL
ALl.
AI
AL _
ALL
ALL
Al I
AI
AL L
ALL
ALL
ALL
ALL
ALL
OVEN
NUMRFP
1 1 -jA
1 135
1146
11^1
1 1 b3
1 149
1 152
1 154
1 147
1 135
1 1 7 J
1 134
* via
i 224
1 1b 1
1 234
1 148
1 15 1
1 1b3
1 149
1 152
1 154
T I MF
OF
PUSH
16 : 02
17 : 49
11:23
1 1 bb
12 32
14 24
14 47
15 14
17 tfo
17 4 1
10 10
17
3 1
40
1 1 bb
12 on
1 1 .29
12.DO
12 20
14 : 24
15 01
15 :23
CHC.
HOI E
# 1
CHC
HOI F
U'l
CHC.
HOLE
*3
CHC
HOLE
*4
stand-
pipe
CAP
CUM
iiml or
MAX I Ml
EMISSIONS,
opaci
SECONDS
%
63
100
7 1
ioo
ba
8b
G 1
100
100
79
100
7 1
fcb
75
100
100
75
75
85
100
b1
30
1ft
40
28
25
07
100
3b
20
72
40
74
35
ft 3
45
63
85
73
100
76
100
-------
COKE OVtN iDPSIDk EMISSIONS OBSERVATIONS
KIDC DEMONSTRA TI DM PWOJFC! - BETHLEHEM STEEL CORPORATION
SPARROWS POINT. MARY I AND
1053 Tuesday. Marcn 31, 1992 15
PUSHING
WiNU
EMISSION
OBSERVERS
WIND
SPEED
OBSERVER
CONTROl
ocs
DATE
BATTERY
INIT1ALS
WEATHER
DIRECTION
MPH
LOCA1 ION
BACKGROUND
SYSTFM
33 1
10/19/9 1
1 1
SBP
CI FAR/OC
SW/NW
5 20
SOU IH
BATTERY
KI DC
332
10/19/9 i
1 1
sen
clear/oc
SW/NW
b 20
SOUTH
BATILR/
Kinc
333
10/?1/91
1 1
SBP
OVERCAST
sc
10-15
SOUTH
BAI ibRY
KIDC
334
10/22/91
1 1
SBP
OVERCAST
NW
5- 10
SOU III
BAI1tRY
KI DC
335
10/22/31
1 1
SBP
nviRCAST
NW
5- 10
SOUTH
BAFTFRV
KIDC
336
10/22/91
11
SBP
OVERCAST
NW
5- lO
SOUTH
BATTERY
KIDC
337
10/22/91
1 1
SBP
OVLRCAST
NW
b- 10
SOU IH
BAITERS
KIDC
333
10/22/9 I
1 1
SBP
OVERCAST
NW
5- 10
SOUTH
BAITERS
KIOC
339
10/22/9 1
1 1
SRP
OVERCAST
NW
5- 10
SOUTH
BA1TERY
KIDC
340
10/ /^/.41
1 1
SBP
OVFRCAST
NW
5 10
SOUTH
HA f 11 RY
Kinc
3-11
io/??/»i
1 1
SRP
nvi-RCAST
NW
5 10
SOUTH
CAT ILRY
K I DC
342
10/22/91
t 1
SBP
OVERCAST
NW
b- 10
SOUTH
BAT1CRY
KIDC
34 3
10/22/91
12
SEP
Clear
St
10- 15
SOU TH
BAT ILRV
5HLNANG
3/. -1
10/22/91
12
SBP
CLEAR
SF
10- 15
SCUTH
BATTERY
SHFNANG
34 5
10/22/91
12
SBP
CLEAR
SL
10- 15
SwUlH
KATTFRY
SHFNANG
3-'. ti
I0/24/91
it / 1 2
SBP
OVkKCASI
SE
15 20
SCU1H
HA 1 IF RY
Kinc
.14 7
10/?4/91
11/1?
SRP
OVFRCAST
SE
15 ?C
SOUTH
BATTERY
SHENANG
:na
10/24/91
1 1/ 12
SBP
OVERCAST
5E
1b 20
SCUTH
BATTERY
K I DC
3 1 '3
10/24/01
li/u'
sen
OVERCAST
SE
15 20
scum
LAI IhRY
KiUC
3 j C
10/24/91
11/12
SBP
OVERCAST
SE
15 20
SCUTH
RATTFRY
KIOC
Ji> 1
10/24/91
1 1/ 12
SHP
UVfcKCAS J
SE
I5-20
SOUTH
EATTERr
SHFNANG
3h2
IO/24/&1
1 1/ IP
SRP
OVFRCAST
SF
15 ?C
SOUTH
OAT 1LRY
KIDC
CHARGING
CUM
HOLE
TIME CMC,
CHG
CHG CHC.
STAND
TIMF or
maximum
LIDS
OVEN
OF HOI e
HOI F
HOI F HOI F
PIPE
EMISSIONS
OPACITY.
O
CD
OFF
NUMBER
PUSH ft 1
*'?
U'A UA
CAP
SECONDS
%
33 1
ALL
M3R
1 7 ¦ 34
59
b5
332
ALL
117 1
1 7 : b /
ao
95
333
ALL
1 14H
11:4?
G9
5h
33-1
ALL
1148
11.51
7 1
75
335
A1 I
1 15 1
K> : J9
4a
45
336
ALL
1 153
12:50
75
55
337
ALL
1 149
15:00
a a
45
338
At I
1 172
15:49
70
100
339
ALL
f t'j2
16.2b
/:j
100
340
At 1
1 135
17 17
45
00
34 1
A I I
1 154
17 39
6 1
100
3 42
ALL
117 1
17.57
12
100
3 13
A1 t
t 2 0 1
' C . 05
:»h
?0
314
At 1
12 11
1fe 13
31
4 b
315
ALL
122 1
1b 2 /
68
100
340
ALL
1 14b
1 1 35
58
70
317
ALL
1234
H 43
100
34 A
At L
t 15 1
1 1 : 59
HO
40
.1-1')
At t
\ 153
12-34
7 1
20
35C
A I I
1 149
14:33
1258
14:42 0
51
20
2j2
ALL
1 172
14 . 59
64
100
-------
COKf OVt-N I UPS IOL tMlbSIONb OBhtKVAI lQNi 10:53 Tyesdtly, March 31. 1392 17
K1UC OEMONSTRA T ION PROJECT 8t 110 Fr!FM STEFI CORPORATION
SPAKRUWb POINI, MARYLAND
PUSHING
Wi NU
LMISSIOr
ORSFRVi KS
WIND
SPECD
OBSTRVr R
CONTROL
QBS
DAT C
BATTERY
INITIALS
WEATHER
OIRkCtKIN
MPH
I 11CAT ION
background
SYSTEM
353
10/24/91
11/1?
SRP
OVtHCASI
SE
15-20
SOUTH
BATTERY
K I DC
3b 4
10/24/91
11/12
S8P
OVERCAST
St
15-20
SOUTH
BA I IERY
KIDC
3b5
10/24/91
I 1
SRP
OVERCAST
SOUTH
10 15
SOJIM
BA11LRY
KIOC
3h«
10/24/91
11
SBP
OVERCAST
SOUTH
10- 15
S0J1H
HA I IfcRY
KIDC
35S7
io/30/ni
11/12
SHP
CLLAR
NC
5 10
SOUTH
BATTERY
KIDC
358
10/30/91
11/12
SBP
CLEAR
NI-
b- 10
SOUTH
RATTFRY
KIOC
350
10/30/91
11/12
SBP
Ct t ftR
NE
5 10
SOUTH
DATTERY
KIDC
36 O
10/30/91
11/12
sbp
CI f AR
NF
5- 10
SOUTH
UA111RY
KIDC
36 1
10/30/91
1 1/12
SBP
CI b AR
NE
5 10
iOUTH
RATTFRy
KIDC
362
10/30/91
11/12
SBP
CLLAR
NE
5-10
SOU I H
BA!IEttY
KIDC
363
10/30/^1
11/1?
SBN
CLEAR
N
lb • 20
SOIJ'H
BATTFRY
SHFNAMG
364
10/30/91
11/12
SEP
CI kAK
N
1b- 20
SOUTH
BATTERY
SHENANG
36b
10/JO/91
1 V12
SQP
CLLAR
N
15-20
SOUTH
RAT URv
SHENANG
366
10/30/91
11/1?
SHP
CI FAR
N
ib-?o
SOU 1 H
OATTCRY
SKCNANG
n*»y
10/30/91
11/12
SBP
Cl FAR
N
15 20
SOUTH
RATTFRY
SHENANG
368
1 l/06/»i
< i
SBP
CL EAR
SW/ St
IS 20
south
BAT FERY
KIDC
369
11/06/91
• 1
SHP
CLCAR
SW/SC
1S-2C)
SOU • H
BAIIhRY
KIDC
370
!1/06/9S
1 1
SBP
CLEAR
SW/SE
15 20
SOUTH
BATTERY
KIDC
J/ t
1 1/00/31
1 1
5EiH
CLEAR
SW/'St
1 b - 20
SUUIH
RA1 i FRY
KIDC
372
11/OG/91
1 1
SBP
Cl FAR
SW/Sl
i 5 ?0
SOUTH
BATTCRY
KIDC
373
11/06/9 1
1 1
SBP
CLEAR
SW/SE
15 20
SOUTH
BA1 1 FRY
K IDC
374
1 1/06/9 1
\2
SBP
CLEAR
SW/Sfc
1 5 - 20
SUUIH
BAT TLRY
SHF.NANC
CHARGING
CUM
HOLE
TI MP CMG
Of iG
CHU CHCa
SI AND-
TIME OF
MAX I MUM
LIOS
OVEN
or HOLE
HOLE
HOLE HULL
PlPfc
EMISSIONS
OPACITY1.
OBS
orr
NIJMBLk1
PUSH ft 1
# 2
*3 "4
CAP
SECONDS
%
353
3
i 152
15:28 0
59
35
35-
ALI
1 13b
1 / . 38
69
bb
30b
ALL
1 15-1
13:05
59
55
356
ALL
1171
18: 20
367
At 1
1 14rt
11:27
82
100
356
ALL
1 151
12 01
68
25
3bb
At I
1 \'j3
12 : 2S
65
30
3CO
ALL
1119
14. 1 3
03
05
361
Al I
1 172
1 4 : 30
73
100
362
Al 1
! lb?
i 4 . 50
ii9
100
nr.n
ALL
1 2b3
15 CO
66
lOO
264
ALL
1 2 63
15 16
43
65
2€>0
ALL
1 2C 1
15.22
2 5
lO
366
2
122 1
15 4 1
0
0
0
14
lO
367
AL I
122 1
15:49
61
lOO
3GA
ALL
1 1 48
11.29
56
IOO
369
3
1 1u1
1 1 . 56
0
67
100
370
ALL
1 153
12 30
45
40
37 1
3
1 149
14 15
o
76
6 b
372
ALL
-.172
14 36
73
100
37 3
ALL
1 152
14:50
63
100
374
ALL
1 224
11.23
61
100
-------
ORS
375
376
:yn
378
379
3UO
381
382
383
381
38b
386
387
388
3 89
390
39 t
317
393
1H4
395
396
HRS
375
376
377
378
379
38C
381
JU2
3B3
384
JB5
38G
387
388
JB'J
390
391
•J92
393
394
395
396
ClKfr OVFM TOPSTDE fcMISSIONS OBSERVATIONS
k fix: nj-MfjN'iTrar ion prooec i bethlehem steel ccrkorajion
SPARROWS POINT. MARYLAND
10:53 Tuesday. March 31, 1992 18
/ 12
/I 2
/ 12
/ 12
1 2
0B5FRVCWJ
INITIALS
E.BP
5BP
SBP
SBP
SBP
bBP
SBP
SBP
SBP
SBP
SBP
SBP
SRP
SBP
SBP
SBP
5BP
SBP
S3P
SBP
SBP
SBP
WFATHFR
CLI.AR
CLEAR
OVERCAST
OVERCAST
UVtKCAbl
OVfcRCASI
OVFRCASI
OVERCAST
OVERCAST
OVFRCAST
OVFRCAST
OVFRCAST
CLEAR
CI t AR
C.I FAR
CLEAR
C! i AR
CI EAR
CLEAR
CI f AK
RAIN
RAIN
WIND
DIRECT ION
SW/Stl
SW/SE
NL
NF
NW
NW
NW
NW
NW
NW
NW
NW
NW
NW
NW
NW
NW
NW
NW
NW
SOUTH
SOUTH
WIND
SPLLD
MPH
lb 20
15 20
5 10
5 10
1b-20
15-20
15-20
15-20
15- 20
15-20
15-20
15 20
20 25
20 25
20-25
20*25
2 'J 2 h
20-95
20 25
2 0 2 b
tb-20
1 b 20
OBSERVER
LOCAlION
SOUTH
SOUTH
oUUIH
SOUTH
SOUTH
SOUTH
SOUTH
SOU I H
SOUTH
SOU I H
SOUTH
SOUTH
SOUTH
SOUTH
SOUTH
SOU I H
SOU I H
SOUTH
SOUTH
SOUTH
SOUTH
SOUTH
BACKGROUND
BAT]FRY
BATTERY
BATTERY
BAT TFRY
BATTERY
BATTERY
BATTFRY
BATTERY
batiery
RATTFRY
BATTfRY
H Ai IERY
BAIIERY
BATTERY
BatiERY
BAIitRY
LiA 1 I LRY
BATTERY
BATTfcRY
BA1 IfcRY
BAT fERY
BAIItRY
PUSHING
EMISSION
CONTROL
SYS1EM
SHENANG
SHfcNANG
SHENANG
SHFNANG
SHENANG
SHENANG
SHCNANG
SHENANG
SHENANG
KIOC
K I DC
K I DC
KIOC
KIOC
KIOC
K1 DC
KIOC
KI DC
K i DC
K I DC
Kmc
KIOC
CHANGING
HOI E
i rns
OFF
OV*N
NUMBER
T 1Mb
OF
PUSH
CHG
HOLE
H 1
CHO
HOLE
HI
CHG
HOLE
#3
CHG
HOLE
*4
stand
PIPE
CAP
CUM
TIMC Of
EMISSIONS.
SLCUNDS
MAXIMUM
OPACITY.
%
2
0
A! L
AIL
At L
At \
ALL
ALL
ALL
ALL
;j
ALL
all
AlL
All
all
A! L
Al I
ALL
ALL
AlL
3
1201
12 1 1
12 16
1226
1 134
1234
1244
12 16
1226
I 148
1 1 •. 1
1 1 b 3
1 151
1 1^3
% My
1 172
1 1b2
1 131)
1 1«j4
117 1
1 148
1 15 1
15 : 26
15:34
12.51
12:58
I 1 : 28
II : 42
1 1 .i>3
1 2 . Ob
12 . 20
J) :45
r; i o
12 39
13 ;05
1 J . 2 1
1 J . \ 3
1-1 ; 08
14 : 28
1b: 02
1b : 39
O
0
16
12
11
00
56
14
1b
3
3b
27
58
33
23
5 I
2 I
80
78
62
6 1
H I
fir*
76
7 2
85
7 1
66
69
7b
5
b
100
Kb
100
65
100
too
35
7b
60
25
100
45
100
100
55
60
85
100
100
100
-------
OUS
397
398
339
400
40 1
4C2
4C3
404
405
406
407
408
409
410
4 1 1
4 12
1 13
4 14
415
4 1G
1 17
OlVj
397
393
399
400
4C 1
402
4C3
4C4
4Cb
405
40 7
4C8
K)9
4 10
-I I l
i 12
4 i 3
1 14
4 15
4 16
4 I 7
COKE OVEN I0PS1UE EMISSIONS ORSFRVAT IONS
K!DC DEMONSTRATION PROJfcCI - BETHLtilLM STEtL CORPORA!ION
SPARROWS POINT, MARVLAND
10 53 Tuesday. March 31. 1992 19
DATE
1 1 /2.V9 1
11/22/91
1 1/22/91
1 1/22/91
1 1/22/H 1
1 t/22/91
1 1/22/91
1 1/22/91
1 1/22/9 1
1 1/22/91
1 1/22/9 1
1 1/22/9 1
1 1/24/91
1 1/24/9 1
1 1 / 2 4 / y 1
1 1/24/9 I
1 1/24/9 I
I 1/24/91
1 1/24/9 1
1 1/24/9 I
1 1/2-1/9 1
CHARGING
HOI F
LIDS
cis-f-
J
3
Al 1
3
J
2
ALL
3
2
\
O
t
A. L
A • I
A. I
Al I
Ai_L
AuL
ALL
ALL
Al t
PUSHING
WIND
EMISSIOf*
OBSERVERS
WINJ
SPEED
OBSERVER
CONTROL
TTCRV
INITIALS
WEATHER
01 RECTION
MPH
I DCAT ION
BACKGROUND
SYSTEM
I
SBP
RAIN
SOUTH
1 5 - 2 ( >
SOUTH
BA T 5 tRY
K|l)C
1
SBP
HA IN
SOU! H
1b-?0
SOUTH
BATTERY
KIOC
1
SBP
RAIN
SOUTH
15-20
SOUTH
BATTERY
KI DC
1
SBP
Rfi IN
SOUTH
15 20
SmilH
BAIltKY
KIDC
1
SBP
RAIN
SOUTH
15 - 20
SOU (H
BAT 1ERY
KIOC
1
SOP
RA IN
SOU I H
15-20
SUUTH
BATTERY
KIOC
1/12
SBP
RAIN
SL
15-20
SOOTH
RATTFRY
shfnanc,
1/ 12
SBP
RAIN
SF
1 b - 20
SOUTH
BATTERY
SHENANU
1/12
SKP
RAIN
sc
15 20
SOUTH
BATTERY
SHENANG
1/ 1 2
SBP
Rfl IN
SF
15 - 20
SOU 1 H
BA! 11 R V
SHENANG
1/ 12
SBP
RAIN
SE
15-20
SOU 1 H
HA! ! {¦ RY
SHFNANG
1/ 1 7
SRP
RAIN
SL
1 b 20
SOUTH
BATTERY
SHENANG
1
SBP
OVERCAST
NW
15-PO
SOUTH
HA W F RY
KIOC
1
SBP
UVfcHCAST
NW
1 b - 20
SOUTH
BATTERY
KIDC
1
SBP
OVERCAST
NW
15-PO
SOU 1 H
BA!1bRY
KIDC
1
SBP
OVERCAST
NW
15-20
SOUTH
mTTrRY
Kf DC
1
SBP
OVERCAST
NW
15-20
SOUTH
DfiTTERY
KIDC
1
SBP
OVERCAST
NW
15 -20
SOUTH
KAIIIRY
KIIJC
1
SBP
OVERCAST
NW
1b-20
SUIJIH
RATTFRY
KIDC
1
SBP
OVERCAST
NW
15-20
SOUTH
RATTFRY
KIDC
1
SBP
OVERCAST
NW
15-20
SOUTH
BA I 1LRY
KIDC
OVEN
NUMBER
TIME
OF
HUSH
CMC
MOLL
tt 1
CHG
HULL
12
CHG
MOLE
*3
CHG
HOLE
STAND
P1 PL
CAP
CUM .
IIMf OF
LM1SSI0NS.
SECONDS
MAXIMUM
OPACITY,
%
1 1 b3
1 149
1 172
1 152
1 135
1 154
1224
1234
1234
12-1-1
122C
1 2 3b
I 146
I 1
i 153
1 140
1172
1 152
1 135
1 154
\ IV 1
13:31
13 :52
14 : 16
14:42
15 : 38
16 23
11:49
I I : 5f)
12 : 32
1 2 . 4 4
»2 50
13 2b
12 50
13 -7
13 3?
13 53
14: 10
14 . 30
14 . -1o
15 :08
1 fc> : 3 2
38
G 1
8b
5 1
SO
7 I
44
2* 1
32
1'8
0
65
61
5G
75
87
69
85
66
90
25
100
100
100
85
100
45
100
10
3 j
0
4b
100
100
100
100
8 b
100
100
45
'00
-------
Section 6
Quenched Coke Discharge & Handling Emissions -
Conventional & KIDC - Database
B-59
-------
t
2
n
4
5
C
7
8
Q
10
I 1
12
13
14
15
10
17
16
iy
20
2 i
22
BS
2
4
5
C
7
6
0
10
i i
1 j
1 4
15
If,
17
1fl
19
20
2 1
22
QUENCHtO COKE DISCHARGE/HANDLING EMISSIONS DATA
KRESS IlEMONSTRATION PRCJLCl liC It iLLMLM STEEL CORPORATION
SPARROWS POINI. MARYLAND
10 5b luesday. March J1. 1992 1
OBSl'^vlks
WI Nf;
SPEED
ORStRVFR
PA 11
0.7/ }9/D I
01/ in/9t
03/19/91
03/ 19/9 1
03/19/91
03/22/91
03/22/91
03/22/9 1
03/22/9t
03/22/01
03/22/91
03/2 2/S 1
03/22/9 I
03/22/3 1
03/26/9 1
03/20/01
OJ/Ju/cM
03/2(5/9 1
03/26/9 1
03/26/9 1
on/?«/q 1
03/26/9 1
OHSf 3
VAFION
START
TIME
bAl1ERY
} 1
1 1
1 1
1 1
1 1
1 1
12
12
t 2
12
1 2
1 1
'.'J
12
1 2
12
< 2
12
1 1
i I
i 1
i 1
COKE
DISCHARGE
OBSEH
VA fION
ENO
T IMf
4ITIALS
WtAfHFR
01 RF r.T ION
MPH
LOCATION
BACKGROUND
LOCATION
r,w
CLEAR
WEST
10 I'O
N
FAS'
CLEAR
WHARF
GW
CLCAR
WEST
10-20
N
F AS f
CLEAR
WHARF
GW
CLE Art
WE SI
lO 20
N
LAST
CI F AM
WHARF
aw
CLEAR
WEST
10 ?o
N
EAST
CI FAR
WHARF
GW
CLfcAW
WEST
10-20
N
EAST
CLEAR
WJ lARf
GW
OC/KAIN
10- lb
CIOUDY
WHAKf
GW
OC/RAIN
in- ir>
CLOUDY
WHARF
GW
OC/RAIN
10- 15
CLOUDY
WHARF
GW
OC/ftftIN
IO lb
CLOUDY
WHARF
GW
OC/RAIN
10" 15
CI niJOY
WHARf
GW
OC/RAIN
10- 15
CIOUDY
WHAHF
UW
OC/RAIN
10- IS
CLOUUY
WHARF
GW
nr/RAiN
10 »5
CI OlJOY
WHARF
GW
OC/RAIN
10 15
CLOUDY
WHARF
r.w
OVERCAST
St
10-15
NORTH
W» IAR f-
GW
OVERCAST
St
10- lb
NORTH
WHARF
(iW
OVERCAST
St
1C- 15
NORTH
WHARF
GW
OVFRCAST
Sf-
10 1
NO
RTil
W» iARF
GW
OVERCAST
sc
10-
NOR 11 1
WHARF
GW
OVCRCAST
SE
lO 1 "-j
NUR 1 M
WHART
C.W
OVERCAST
SC
1C- 1 &
NURIH
WHARF
GW
OVERCAST
SE
10 15
NOR? H
WHARF
KKLSS
BOX
MUMBTR
CUMUIATIVF
EMISSION
TIM!
SECONDS
MAX IMUM
opacity
¦L
K IOC
COOLING
TIME
MR MIN
HOI
SPOTS
Y/N COMMtNTS
1 300
1 338
i 354
14 10
143H
12 19
1248
1 254
1 328
133h
! "|4«S
14 03
1426
14 39
1 1 33
1212
i 223
124C
125G
1305
1322
1332
f 301
1339
1355
14 1 1
14 39
12 20
1249
125b
I 3 JO
13 3G
134 8
1 J 40
1428
144 2
1 1 30
1213
1 2 30
124 1
1257
13Cb
1323
1333
6ft
121
49
43
50
O
O
O
o
0
o
0
0
0
\C,
IE
10
1 'j
o
o
o
14
O
O
1U
10
15
O
0
o
O
O
o
o
o
o
5
10
5
b
0
o
o
10
steam only
SItAM ONLY
-------
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14 7
14 A
14 J
150
Ifi 1
152
153
154
OBS
133
134
13b
136
137
13 9
139
140
14 \
14 2
u
Ml
14b
i 1G
14 7
14H
149
ISO
1h 1
1fi2
103
lb 4
QUFNCHF3 COKE DTSOHARGE/HANUlING EMISSIONS DATA
KRESS DEMONSTRATION PROOFCT • BETHLEHEM SI E11. CORPORATION
SPARROWS POINT. MARYLAND
10:SG Tuesday. March 31, 1992 7
W1KD
COKL
OATE
o^/13/qi
Ob/13/91
05/13/91
05/13/91
05/13/91
Ob/ 14/a 1
05/14/91
Ob/14/91
Ob/14/9 I
05/14/91
05/14/91
05/ 14/9 I
05/ 14/9 I
OH/ 14/91
Ob/ 14/y 1
C5/3 1/9 1
Ob/2 1/9 1
05/21/91
0b/2 1/9 1
05/2 1/9 1
05/21/91
05/21/91
OnSTRVt. RS
Wl N1J
S^EEI)
OGSL'RVL R
DISCHA*
BATTFRV
INITIALS
WEATHER
DIRFCTION
MPH
1OCATIUN
BACKORUUNO
IOCATIE
11/12
GW
CLEAR
SI
3-6
NORTH
CLEAR
WHARE
1 1/12
GW
CLEAR
5E
3 6
NORTH
CI FAR
WHARF
11/19
GW
CLEAR
SE
3 - G
NORTH
CLLAR
WHARF
11/12
GW
CI 1 AK
St
3-6
NORTH
CLEAR
WHARF
11/12
GW
CLCAR
St
3 6
NORfH
CLEAR
WHARF
11/12
uw
CLEAR
NW
6- 12
ne
CLEAR
WHARF
11/12
GW
CLEAR
NW
6- 1?
m
CI FAR
WHARF
11/12
GW
CLLAR
NW
6- 12
NL
CLEAR
WHARF
11/12
GW
CLEAR
NW
6-12
Nb
CLEAR
WHARF
11/12
GW
CI EAR
NW
6- 1*2
Nb
CLEAR
WHARF
11/12
GW
CLEAR
NW
b - 12
Nb
CLEAR
WHARF
11/ 1 ^
GW
CI t AK
NW
6 12
Nb
CI FAR
WHARF
11/12
GW
CLEAR
NW
6 12
NE
CLEAR
WHARF
11/12
GW
CLLAR
NW
6 12
Nb
CLEAR
WHARF
11/12
GW
CI EAR
NW
6- 12
NE
Cl EAR
WHARF
11/12
GW
CLEAR
SE
6- 12
NORTH
CLEAR
WHARF
11/12
GW
CLLAR
bfc
b- 12
NORTH
CLEAR
WHARF
11/12
GW
CLLAR
SE
12
NORTH
01 FAR
WHARF
1 1/ 12
GW
CLEAR
SE
G- 12
NORTH
CLEAR
WHARF
11/12
GW
CLEAR
SI
b 12
NORTH
CLEAR
WHARF
11/12
GW
CLEAR
S6
6- 12
NOR f H
CLEAR
WHARF
11/12
GW
CLEAR
SE
b 12
NORTH
CLEAR
WHARF
G3SER
ORSFR
niiMlJI ATTVF
VATION
VATION
KRESS
EMISSION
MAXIMUM
START
END
BOX
TIME
OPACITY
TIME
TIME
NUMBER
SECONDS
%
12 23
1224
0
O
1233
1234
0
o
I2h4
1?bb
0
0
1320
1320
0
0
1328
1328
0
o
1 135
1 1 30
o
o
1 144
1 145
0
0
1 Ib4
1 Ibb
0
0
1 2C2
1202
0
o
123b
123b
0
0
1 :> 1 y
ILMtt
c
0
13C2
1303
o
o
1306
1308
0
0
13 1b
1 3 15
0
o
1339
1340
0
0
1 1 'j 4
1 1b4
0
0
t ?nn
1209
0
0
1 226
1226
0
0
1? 16
iV At
0
0
13 10
131 1
0
0
1321
132 1
0
0
1 J JO
133 /
0
o
K I DC
COni I N(>
TIME
HR:MIN
MO!
SPOTS
V/N
COMMENIS
-------
QUENChFD COKE DISCHARGE/HANDLING EMISSIONS DATA
K^C'iS DCMONblKATION PROJECT - BET HIEHtM bltlL CORPORA T I ON
SPAKNCJWS POINT. MARYLAND
10:56 Tuesday. March 31, 199:? R
WIND
COkF
CHbfRVr
*S
WIND
SPIED
OBSERVER
DI SCHARGf
OBS
DA : F
BAI 1fcNV
INI HALS WFATMfR
niRFC.
T ION
MPH
IDCATION
BACKGROUND
LOCATION
1SS
05/2I/Qt
1 1 / 12
uw
CLLAR
5 ;
b- 1 2
N2RTH
Cl FAR
WHARF
156
05/21/91
11/12
GW
CLfcAR
Sb
6- 12
NORTH
Cl EAR
WHARF
157
Ob/2 1/SI
11/12
GW
CLEAR
St
fe- 1?
NORTH
CLtAR
WHARF
15a
OS/22/91
11/12
GW
SC
6 12
NORTH
WHARF
1G3
05/22/91
11/12
GW
SF
6- 1?
NCRTH
WHART
160
05/22/S1
11/12
GW
SF
6- 1?
NORTH
WHARI
1G1
OS/23/9 1
11/12
GW
SF
4-8
NORTH
WHARF
162
05/23/91
1 1/12
GW
5E
4 8
NORTH
WHARF
"•03
05/23/01
11/12
GW
bt
4 8
NUKUI
WHARF
164
05/23/91
11/12
GW
SE
4-8
NORTH
WHARF
165
05/23/91
11/12
GW
SF
4 -8
NORTH
WHARF
•6S
05/21/?) 1
11/1?
GW
SC
4 0
NOR TH
WHARF
167
05/23/9 1
11/12
GW
SE
4 B
NOR I H
WHARF
1 £8
05/28/9 1
11/12
GW
OVLKCA'jl
NW
4 9
NOR IH
HAZY
WHARF
-by
05/23/B 1
11/12
GW
OvFRCAST
NW
4 9
NOR IH
HAZY
WHART
170
05/23/9 1
'1/12
GW
OVFRCAST
NW
4 9
NORTH
HAZY
WHARF
• 7 \
Oh/ ?a/b
1 'J 50
1350
0
O
156
1 358
1 359
o
O
157
1418
1418
()
0
158
1323
1 324
0
0
159
1349
1350
0
o
160
1109
1409
o
0
161
1258
1 ?59
o
0
162
1308
1 308
0
0
163
* -J 1 1
1 J17
<)
o
164
1321
1325
0
0
165
1 33'J
1 34C
o
0
4 -105
• 405
o
0
1G7
14 11
14 12
o
0
iGfl
1 1 3C
1 U 1
o
o
169
1228
1229
2 1
io
1 70
1245
1246
0
o
'71
1253
1253
o
0
17?
1310
1311
o •
0
173
13 19
1319
0
o
1 / 4
1334
1335
0
o
175
144b
1446
0
0
*,76
1458
1458
15
1b
-------
OUtNCHCD COKC DISCHARGE/HANDtING EMISSIONS DATA
KRESS DEMONSTRAI/ON PROJECI - BETHLEHEM SIttL COHPQRATIO.N
SPARROWS POINT. MARYLAND
IO.'jH luesrJay, March :i1 , 1992 9
WIND
COKE
OBSERVERS
WIND
SKcLJ
UHStRVcK
DISCHARGF
CBS
DAT t
BATTERY
INITIALS WEATHER
Dl
RLCTIQN
MPH
LOCAI ICN
BACKGROUND
L0CA1ION
177
05/29/9 1
1 1/ 12
GW
CI EAR
SF
£- 1 ?
NORTH
CI FAR
WHARF
178
05/29/91
11/12
r, w
C.I FAR
SF
6- 12
NORTH
CLEAR
WHART
179
05/29/91
1 1/12
gw
CI FAR
St
6- 12
NOR 1 H
CLEAR
WHARF
tea
05/29/9 1
11/12
GW
CI F AR
SE
o 12
NORTH
CLLAK
WHARH
18 1
05/23/01
11/12
GW
CLEAR
SC
b 12
NORIH
CLEAR
WHARf-
182
C5/29/91
1 1/12
GW
CLEAR
sc
6-12
NOR Hi
CLEAR
WHARF
183
G5/29/9\
1 1/ 12
5,
o
o
*9 1
1 225
1 2 2G
0
o
192
1237
12 38
0
0
193
12 4 9
! 249
0
0
104
»30P
130G
0
0
19b
1342
1342
0
0
191.
1402
1403
0
o
197
1409
14 10
0
o
tea
} !4G
1 146
0
<)
-------
OBS
199
?oo
201
202
2 OU
204
205
?06
207
208
S09
2 10
2 1 1
2 12
2 I J
2 1 I
2 15
2 1 to
2 1 7
2 18
2 19
s?o
DBS
199
200
201
202
203
204
2 Ob
206
207
208
209
2 10
2 1 1
2 12
2 13
7 14
2 15
? 16
217
2 1U
2 19
22<)
OUtNCHf3 COKE DI SCHARGb /HANDL 1NG EMISSIONS DATA
KRFSS DEMONSTRATION PROJFCT - BETHLEHEM STEEL CORPORATION
SPARROWS POINT, MARYLAND
10:56 Tunsday, Marcn 31. 1902 10
DATE
06/04/91
CR/04/9 t
06/04/91
06/04/91
06/O'i/ai
06/04/91
06/04/91
0G/04/91
06/04/91
Ob/10/91
06/10/91
06/10/01
Ob/10/9 1
06/tO/91
06/10/9 1
Ob/10/D•
06/10/91
Ob/10/91
06/10/^1
06/13/91
00/13/91
06/ 13/91
OtSSER
VA1 I(jN
START
TIME
WIND
OBSERVERS
WIND
SPEED
OBSERVER
BATTERY
INITIAL
S WLAfHLR
DIRECTION
MPH
LOCAiION
bACKGRC
11/12
GW
CLEAR
NF
9-15
NORTH
CLEAR
11/1?
GW
CLLAR
NE
9 15
NOR fH
Cl EAR
11/12
GW
CLEAR
NE
9- 15
NOR 1 H
CLEAR
1 1/12
GW
CLEAR
NE
9- lb
NURIH
Cl FAR
11/12
GW
Ct FAR
NE
9- lb
NORTH
CLEAR
1 1/12
nw
CLEAR
NE
9-15
NORTH
CLEAR
1 1/ 12
GW
CLEAR
NE
9- 15
NOR HI
CLLAK
11/12
GW
clear
NL
9 15
NORTH
CLEAR
1 1/12
GW
CI EAR
Nt
9- 1b
NORTH
Cl EAR
11/12
GW
CI FAR
NW
b ¦ 10
NORTH
Cl FAR
11/12
GW
CI FAR
NW
5- 10
NORTH
CLCftR
11/12
GW
Ct FAR
NW
5 10
NORTH
CLLAR
11/12
GW
CLLAK
NW
5- 10
NORTH
Cl 1- AR
11/12
GW
C 1 ?AR
NW
S- 10
NORTH
CLEAR
11/12
GW
clear
NW
b 10
NORTH
CLEAR
11/12
GW
CLEAR
NW
b- 10
NORTH
CLEAR
11/12
GW
Cl FAR
NW
5 10
NORTH
CLEAR
11/12
GW
Ct FAR
NW
b- 10
NORTH
CLEAR
11/12
GW
CLEAR
NW
5 10
NORTH
CLLAR
11/12
GW
CLEAR
NW
G 12
NOR IH
CLEAR
1 1/ 12
GW
Cl fcAR
NW
0 12
NORTH
CLEAR
11/12
GW
CLEAR
NW
6- 1?
NORTH
Cl FAR
R
CUMULAIIVL
KIOC
II ION
KRL5S
EMISSION
MAXIMUM
COOt ING
HOT
NU
HOX
1 IME
OPACITY
TIMF
SPOTS
' IME
NUMBER
SECONDS
%
HR:MIN
V/N COMMfNT
5
COKE
0 I SCHARGf*
LOCAT ION
WHARr
Wl lARh
WHARF
WHARF
WHARF
WHARF
WHARF
WHARF
WHARF
WHARf
WHARF
WHARF
WHARF
WHARF
WHARF
Wl 1AK*
WHARF
WHARF
WHARF
WHARF
WHARF
W* iARF
12 1 1
1249
1301
1312
1328
1354
NOb
M 15
14 2i>
I 132
1 156
1206
12 25
1249
1 JOJ
13 10
13 19
1335
1342
1 U4
1 IbS
1203
1212
I 2 b()
1301
1312
1329
13b5
140V
14 15
1426
1133
I 156
1208
1225
1250
1304
13 11
13 19
1336
134 3
1 1 J'j
1 Ibb
12C4
O
o
0
o
0
0
0
0
o
o
0
0
18
0
o
o
26
14
16
0
O
O
0
O
O
0
o
o
0
o
0
o
0
G
1G
O
O
c
20
10
10
O
O
0
-------
ODS
22 I
222
22 3
224
22\j
226
227
226
229
230
231
232
234
235
2 36
2 37
2 38
2'J 9
240
24 1
242
DBS
22 1
222
223
224
??h
226
227
OOfs
229
2 30
2 3 1
23'J
23*3
2Jt>
2 36
237
238
2 39
240
24 1
2 4?
QULNCHFO COKt DISCMARGL/MANJLING LMlbblONS DATA
1
06/ 17/9 1
06/17/9 1
06/17/91
06/ 17/91
06/17/91
06/ 18/91
06/ 1b/91
06/ 16/91
06/ 16/91
06/ I ft/91
BATTER*
1/12
1/12
1/12
1/12
1/12
1/12
1/12
1/12
1/12
1/12
1/12
1/12
1/1?
1/12
1/12
1/12
1/12
1/12
1/12
1/12
1/12
1/1?
OBSERVERS
INITIAIS
CW
GW
GW
GW
GW
GW
GW
GW
GW
GW
Cw
Gw
C*
Gw
GW
GW
CW
GW
GW
GW
GW
GW
WIND
COKE
WIND
SPEED
OBSERVER
n T SCHARGt
W|-AlHfcK
UiRLCI1UN
MPM
LOCATION
BACKGROUND
LOCATION
CLEAR
NW
6 12
NORTH
CLEAR
WHARF
CLEAR
NW
0 12
NORTH
CLEAR
WHARF
CLEAR
NW
6-12
NORTH
CI EAR
WHARF
CLEAR
NW
6-12
NORTH
CLEAR
WHARF
Ct FAR
NW
6- 12
NOR nt
Cl EAR
WHARF
CLEAR
NW
6-12
NORTH
CLEAR
WHARF
a EAR
NW
b- 12
NORTH
CLCAR
WHARF
CI t AH
NE
6 12
NOR \ H
SCT
Cl PS
WHARF
CI FAR
Nfc
b 12
NORTH
SC!
CLOS
WHARF
CLtAR
NE
6 1 ?
NORTH
SCT
Ct OS
WHAKf
ct E-AR
NE
6 12
NORTH
SCT
Cl OS
WHARF
clear
NE
6-1?
NOR I H
SCF
CLDS
WHARF
CLEAR
Nfc
6- 1 2
NORTH
SCT
Cl OS
WHARf-
Ct EAR
NE
6- 1 2
NORTH
SCT
CLUS
WHARF
CLEAR
Nt
6 *2
NORTH
SCT
Cl OS
WHARF
CLCAR
NE
6-1?
NORTH
SCI
CLL3S
WHARf
Cl FAR
NE
6- 12
NORTH
SCT
CLOS
WHARt-
OVERCAST
St
5 10
NOR I H
Cl OtJUY
WHARF
OVERCAS1
Sb
- 10
NORTH
CLOUDY
WHARF
OVERCAST
SE
5- 10
NORTH
ClOUOY
WHARF
OVERCAST
SE
b- 10
NORTH
CLOUDY
WHARF
OVLRCAS 1
Sl
5 to
NORl i i
CLOUDY
WHAKh
OiiSER
~USER
CUMULA7I Vfr
VAT ION
VATTON
KRFSS
LMISS1UN
MAXIMUM
START
END
BOX
TIME
0PAC11Y
TIME
T 1Mb
NUMBbR
iLCONDS
%
12 17
12 10
0
0
1249
12'oO
o
0
1259
1259
0
o
1308
1309
0
0
1319
13 19
o
0
1323
1324
0
0
13ti4
1 ii'o'j
0
0
1 137
1138
0
0
1 146
1 14 8
0
0
120/
1200
o
c
1230
1 2 30
o
c
1 2 'J 7
1236
0
6
I15G
1250
i 3
10
1301
1301
9
1 5
1 joy
1309
O
c
1332
1332
0
r.
1354
1354
O
0
1 127
1 128
0
o
1 14-
1 144
o
c
1206
1206
0
G
1227
\ ?2ft
0
0
12-16
1246
0
0
K I DC
COOLING
1 iME
HR.MIN
HG1
SHUTS
Y/N
COMMENTS
-------
QUENCHCO COKE OISCHARGE/HANDLING EMibblONS UA i A
KRC'jO demonstration project qcthlehem steel CORPORATION
SPARROWS POINT, MARYLAND
10:56 Iuui>day. March 31, 1992 12
WIND
CUKE
ORSTRVCR
0
WINE
IsRLCD
OBSERVER
DISCHARGE
ORS
DATF
KA1 fFRY
initials
WEAIHER
DIRECTION MPH
L0CATION
BACKGROUND
I OCA I ION
243
06/ 18/91
1 1/1?
GW
OVERCAST
SET
5- 10
NORTH
01 OLJfJV
WHARh
214
06/ 18/9 1
1 1/12
GW
overcast
SE
5 10
NORTH
CLOUDY
WHARF
245
06/ lfi/91
11/12
C.W
OVF RCAST
5E
5 10
NOR IN
CLOUDY
WHARF
?4f,
OS/lfi/91
1 1/12
GW
OVERCAST
Sf
5- 10
NOR r H
CIOODY
WHARF
247
CG/ 18/01
1 M 12
GW
OVERCAST
SL
b- 10
NOR IH
CLOUDY
WHARF
246
06/24/91
1 1/12
GW
CLEAR
NW
5- 10
NORTH
WHART
249
06/24/91
1 1/12
GW
CI FAR
NW
5- 10
NOR IH
WHARF
250
06/24/9 1
1 1/12
GW
CLEAR
NW
5 10
NOR 1 H
WHART
251
OG/24/9 1
1 1/12
GW
CI FAR
NW
h- 10
NORTH
WHARF
252
06/24/91
1 1/12
GW
CLEAR
NW
h- 10
NORTH
WHART
253
06/24/01
1 1/ 12
GW
CLEAR
•NW
r>- IO
r.DG T H
WHARf
254
CS/24/9 1
11/12
GW
CLEAR
NW
5 10
NORTH
WHARf
255
06/24/9 1
1 1/ 12
GW
CLL AR
NW
b- IO
NOR 1 H
WHARF
2 50
CC/24/9 1
1 1/ 12
GW
CI MR
NW
5- IO
\0R T H
WHART
257
Co/24/9 1
11/12
GW
C.i - AR
NW
r.-iO
NORIH
WHARF
C6/26/9I
1 1/ 12
GW
CI FAR
SL
a- 12
NOR I M
CLEAR
WHARF
2 59
CS/26/9 1
11/12
CW
CLCAR
SL
B 12
SUM 1 H
CLEAR
WHARF
260
CC/26/91
1 1/ 12
GW
CLEAR
SE
B- 12
NOR IH
CI FAR
WHARF
20 1
Oo/Vb/fll
1 1/12
GW
CLEAR
SL
a -12
NORTH
CI FAR
WHARF
2b2
CG/2G/a 1
11/12
GW
CI F AH
SE
a 12
NORTH
clear
WHART
203
06/26/9 1
1 1/12
GW
CI f AR
SF
fl- 12
NORTH
CLEAR
WHARr
204
00/26/9I
1 '/ 12
GW
CLEAR
SE
a -12
NORTH
clear
WHARF
. UHSTR
GbStW
CUMUlA!iVh
KIOC
VAT ION
VAT ION
KKL55
fcMl5SI ON
MAX!MUM
CHOI I NO
HOT
$TA.}I
END
UOX
TIME
opacity
T IMF
r.priT
UBS
I IMt
1 I Mh
NUMBER
SECONDS
%
HR:MIN
V/N COMMUNIS
243
1303
1 303
0
0
244
1337
1 33 /
0
o
245
134b
1345
0
0
246
140b
1405
0
0
24 7
1426
14 26
0
0
248
1127
1 <27
0
0
24N
1 138
1 138
0
0
2bO
1 14b
1 146
0
0
;>*> l
1206
1',»(>fi
0
0
252
1 246
124 6
0
o
V» J
1 Ju4
1 j;>4
0
o
2 b 4
1J 13
13 13
o
0
2bb
1327
132 7
0
0
25G
1336
1336
o
o
1353
1 35.1
0
0
258
I 256
1250
! 5
0
1 307
1307
20
io
260
1325
1325
0
0
2b 1
133b
1336
0
0
262
1319
134 8
0
0
263
1403
1403
0
0
264
1424
1 124
0
0
-------
OBS
265
2GC
267
268
'ioy
:>vo
27 1
2/2
273
274
276
27 7
J 78
2?9
260
:>B i
282
263
264
58b
200
OBS
265
266
267
260
269
2/0
271
2 7 2
273
274
? r*>
27G
277
?7B
279
2H0
28 I
282
283
264
2Bb
2B6
UUtNCHED CC.KC DI SCHARGE/HANDt I NG EMISSIONS DATA
KRESS DEMONSTRATION PROJECT - BE THLtHEM SltC L CORPORATION
SPARROWS POINT. MARYLAND
10;b6 l-esaay, March J1 , iyy2 1U
OBSERVERS
ua r c
EATTERY
INITIAI S
WEAThfcR
C6/26/91
11/12
GW
clear
00/20/91
11/12
GW
Cl t AH
06/26/91
1 1/12
GW
CLEAR
C7/01/91
11/12
GW
UVFRCAST
O '/O 1/91
11/12
GW
OVERCAST
0 J/O1/91
1 1/12
GW
OVFRCAST
C7/0I/91
It/ 12
GW
OVERCAST
C 7/0 l/'S 1
11/12
GW
OVFRCAST
C7/01/01
1 1/12
GW
OVFRCAS!
0V01/91
11/12
10
1452
1452
0
0
1 125
1126
0
0
1 139
1 140
o
0
1 150
1 150
10
10
1204
1204
0
0
1223
1223
10
1b
1229
1229
0
0
12b?
121)2
0
0
1 DOG
13 or.
0
0
1318
1318
0
0
1324
1324
0
o
14 4fc
14-16
0
o
1507
1507
0
c
1'j1L
1515
0
o
1522
1522
0
0
1529
1530
0
0
1556
Ibbb
0
o
16 15
16 15
0
o
1626
1626
0
0
1640
1640
0
c
K I DC
COOl TNG
TIME
HR.M1N
HOI
SPOTS
Y/N CQMMCNTS
COKL
O I SCItARGE
LOCATION
WHARF
WHARf
Wf lARt
WHARF
W» lARf
WHARF
WHARF
WHARF
WHART
WHARF
WHARF
WHARF
WHARF
WHARF
WHARr
WHARF
WMARf
WHARF
WHARF
WHARF
WHARF
WHARF
-------
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-------
OBS
309
3 lO
31 1
3 12
313
3 M
315
316
J 17
3 1H
J 19
320
32 1
322
323
324
32b
3 20
3 2 7
326
J 29
330
DBS
309
310
311
31?
313
314
315
316
3 17
A 1ft
319
320
3? I
3 n
\ -J i
:\J4
325
326
327
328
329
330
QlJh NCHF3 COKF DI SCHARGh/HANOI T MG FMISSTCNS DATA 10 5G Tuesday. March 31, 1932 ib
KRFSS DEMONSTRATION PROJECT - BETHLEHEM STEEL CORPORATION
SPARROWS POINT. MARYLAND
DATE
07 / 15/31
07/15/91
07/15/91
07/ 15/91
07/ 15/91
07/ 15/91
07/ 15/91
07/15/91
07/18/91
07/ 18/9 1
07/ 18/91
'Jf/ 18/9 1
07/ 18/9 1
07/ 1fi/91
07/ 16/91
07/tfi/9i
07/ 16/9 1
07/16/91
07/22/91
07/22/91
07/22/91
07/22/91
ORSER
VATTON
S I ART
TIME
1237
1243
12bO
1309
1316
133?
1 349
1359
1 1 ? 7
I 15 t
1204
I 2 3 -J
1 32 I
1 33 1
MC-l
14 12
1429
1438
1 130
1 157
1272
1237
WIND
OBSERVCRS
WIND
SPEED
OBSLRVER
DAT ? fcH i
INIrI ALS
Wt-A 1 Htk
UIRfcCIION
MPH
LOCATION
BACKGROUND
11/12
GW
CLEAR
Nfc
b- lO
NOR 1 H
CLEAR
<1/1 2
GW
ct far
NF
5 10
NORTH
CLEAR
11/12
(?w
C| FAR
NE
b- 10
NORTH
CLEAR
11/12
GW
CLEAR
NL
5 10
NO k'IH
CI LAR
11/12
GW
CLEAR
NE
5 10
NORTH
CLEAR
1 1/12
GW
CLEAR
NE
b 10
WURTH
CI EAR
11/12
GW
CLLAR
NE
b- 10
NORTH
C. EAR
11/12
GW
CLfcAR
NE
5-10
NORTH
CI FAR
11/12
GW
CLfcAR
SW
4 9
NORTH
11/12
GW
CI EAR
SW
4 9
NORTH
11/12
GW
CLEAR
SW
4 9
NORTH
1 1/12
GW
CI FAR
SW
4-9
NORTH
11/12
GW
CI FAR
SW
4-n
NORTH
11/1?
GW
CLEAR
sw
4 9
NORTH
11/12
GW
CI FAR
sw
4 9
NORTH
11/12
CW
Clear
SW
4-9
NOR I f (
11/12
Gw
clear
sw
4 9
NURIH
11/12
Gto
Clear
sw
4-9
NORTH
11/12
GW
clear
SE
b - 10
NORTH
HA/v
11/12
GW
CLEAR
SE
'j - 10
NORTH
HAZY
11/12
GW
clear
SL
5- 10
NORTH
HA 2 Y
11/12
GW
clear
SE
5- 10
NORTH
HAZY
COKE
01 SCHARGj-
LOCATION
WHARI-
WHARF
WHARr
WMAKh
WHAKf-
WHARF
WHARF
WHARF
wharf
WHARF
WHARF
WHART
WHART
WHARF
WHARF
WHARF
WHARF
WHARF
WHARF
WHARF
WHARF
WHARF
ORSFR
VATION
FND
T1MF
KRESS
BOX
NUMBER
r.jy.m ative
EMISSION
TIME
SLCCNDS
MAXIMUM
OPACITY
%
K IOC
COOLING
TIME
HR MIN
HOT
SPOT j
Y/N
COMMENTS
1237 0 O
1243 0 0
1250 0 0
1309 0 0
1317 0 O
1332 0 O
1349 u 0
1400 . 0 0
1 126 0 O
115 1 0 O
1204 0 0
1?3 4 0 (J
132? 0 O
133 1 0 0
MO'i 0 0
14 12 O 0
14 30 0 i)
14 36 0 O
1130 0 0
1157 0 0
1222 0 0
1239 0 0
-------
OUrNCHFD COKE DISCHARGE/HANDLING EMISSIONS. OATA 10.56 Tuesday. March 31. 1992 16
KRESS DEMONSTRATION PROJECT - BETHLEHEM STfctl CORPORATION
SPARROWS PUJNI. MARYLAND
WIND
COKfc
OBSERVERS
WIND
SPEED
DaSERVfcR
DISCHARGE
OBS
DATE
BATTERY
IN]TIAL
!a WIAIHLK
D1RLC
I i UN
MHH
LOCAI 1UN
BACKGROUND
LOCATION
331
C7/22/91
1 1/12
GW
CLEAR
SE
5-10
NORTH
HAZY
WHARF
33?
07/??/91
11/12
GW
Ci f AH
SI
5- 10
NORTH
HAZY
WHARF
33a
07/22/91
1 1/12
GW
CLCAR
St
5 10
NORTH
HA7V
WHARF
334
01/22/31
1 1/ 12
GW
CLEAR
St
5-10
NORTH
HA / Y
WHARF-
335
07/22/91
1 1/12
GW
Ci t AR
SE
5- tO
NOR r H
HAZY
WHART
336
C7/22/91
11/
12
GW
CLEAR
Sfc
5- 10
NORTH
HAZY
WHARF
JJ/
07/25/91
11/
12
GW
OC.RAIN
sw
4 10
north
OC ,ClOY
KIOC
A3U
0//25/91
11/
12
GW
OC.RAIN
sw
4 10
north
OC . CLDY
WHARF
339
C7/25/91
1 1/ 1?
GW
OC.RAIN
Sw
4-10
NORTH
OC.CLDY
WHARF
3-iO
0//25/31
» 1/ 12
GW
OC.RAIN
sw
4 1Q
NORTH
OC.C.LDY
WHARF
3 4 1
07/25/91
1 1/
15
GW
OC.RAIN
SW
4 10
NORTH
OC,CLOY
Wt 1ARF
34?
C / / 2 b / 9 1
11/
12
GW
OC.RAIN
sw
4 - tO
NORTH
oc.Cloy
WHARF
343
07/25/9 1
» 1
1204
1204
10
5
352
• 204
1204
6
5
-------
OBS
353
fif>4
355
356
357
356
359
300
3G1
302
363
36-1
366
367
30b
3*>9
3 70
3 7 1
372
373
3 7'J
DBS
353
354
3b5
356
357
3b8
359
3GO
3b 1
36;
fr>
r-f.4
~r>b
36G
30 7
36fc
369
37<>
37 1
37?
J rj
374
QUFNCHI-D COKE OISCHARGE/HANDLING EMISSIONS DATA
KRESS DEMONSTRATION PROJECT - BETHLEHEM STEEL CORPORATION
SPAKHOWb HUINI . MANY I AND
10 bb Tuesday. March 31, 1992 17
0B5FRVFRS
WI Nl.)
SPfefeD
OKSFRVER
DATE
tiATTERY
INITIAL
S WLATHfcK
DIRECTION MPH
LOCAIION
BACKGROUND
07/29/91
1 1/ 1?
SBP
RAIN
NE
b 10
NORTH
BATItRY
07/29/9 1
1 1/ 1?
REA
RAIN
NE
10
NOR 111
HA)1fcRY
07/29/91
1 1/12
r, w
OC.RAIN
NE
b 10
NORTH
CLOUDY
07/29/91
1 1/12
SBP
RAIN
NF
b 10
NOKIH
BATIfcKY
07/20/0 1
11/1?
RL A
RAIN
NL
10
NORTH
RATTFRY
07/20/91
1 1/ 12
GW
OC.RAIN
NE
5-10
NORTH
CLOUDY
07/29/91
1 1/12
SBP
RAIN
Ni
b- 10
NUKTH
BATTERY
07/20/9 1
11/12
RfcA
RAIN
NH
10
NORTH
BATTFRY
07/29/91
11/12
GW
0C.RA1N
Nh
b- 10
NOR TN
CIOUPY
07/29/91
11/12
GW
OC,RAIN
Nt
5- 10
NORTH
CIOUOY
C//29/9 1
11/12
GW
OC.RAIN
NT
5- 10
NOR III
CL OUDY
07/29/9 1
11/12
GW
OC . RAIN
NF
b 10
NORTI i
CLOUDY
07/29/9 1
11/12
GW
OC.RAIN
NE
5 10
NOR f 1'
CLOUDY
C7/29/S1
1 1/12
GW
OC .RAIN
NE
3 10
NORTH
CIOUDY
07/30/91
11/12
GW
UVtKCA^1
St
b - 10
NORTH
CIOUDY
C / /30/91
1 1/12
GW
OVERCAST
SF
5- 10
NORTH
CLOUDY
07/30/9'
1 1 / 1 ?
GW
OVHJCASr
5F
5 10
NORTH
CIOUDY
07/30/9 1
1 1/12
GW
OVERCASI
Sc
5-10
MORI H
CLOUDY
C7/3G/9 1
1 1/12
GW
OVLKCAS1
Sr
5- 10
NORTH
CIOUDY
C//30/9 1
11/12
GW
OVERCAST
SE
5- 10
NORTH
CLOUDY
07/30/91
1 1/ 12
GW
UVfcRCASr
SE
5 10
NORTH
CLOUDY
C 7/30/91
11/12
GW
OVFRCAST
SC
b- 10
NORTH
CLOUDY
OBSER
OBStR
CUMULATIVE
K1UC
VATICN
VAT]0N
KRESS
EMISSION
MAXIMUM
COOLING
HOI
START
END
BOX
TIME
OPACITY
T IMF
SPOTS
TIME
TIME
NIJMBE R
SECONDS
%
Hfi.MIN
v/N Cl'JMMf
N 1 S
1232
1232
O
a
12*2
1232
0
o
1232
1232
O
o
1250
1250
o
o
12bO
1250
o
o
1250
1250
0
0
1309
1309
2 2
5
1 309
1309
2 2
5
1309
1 J09
1 1
15
1 4 ?8
1429
0
O
144?
144?
14
s
i iia
14 48
10
20
1500
1 soo
O
0
1514
1 5 ' 4
o
0
1144
1 1 4 1
o
O
1 1b?
1 153
11
10
1 20fc
1 207
1 236
1237
i.i no
1.1.10
1345
134 5
1
-------
OBS
375
376
377
378
37D
¦mo
3a 1
JU2
383
384
3B5
386
387
388
AHH
;jyo
39 1
39?
303
395
396
005
375
376
377
378
379
380
28 »
3B2
363
JIM
3B5
3B6
3fi?
308
389
390
33 1
302
323
394
39b
306
QUENCHED COKE DI SCHARGk/l lANOL I Nw
GW
GW
GW
CW
CW
GW
GW
GW
GW
GW
KRESS
BOX
NUMBER
WFA 1 Ht'R
OVERCAST
CLEAR
CLEAR
CLEAR
CI EAR
CLEAR
CLEAR
CLEAR
clear
CLEAR
ci far
CI fcAR
CLEAR
CI f AW
Cl FAR
CLEAR
clcar
Cl hAH
CL EAR
Cl I AR
Cl. F AR
CLhAW
CUMULATIVE
LMI SSION
TIME
SECONDS
WIND
SPEED
OOSCRVER
REC1 ION
MPH
LOCATION
liACKORUI
SF
b- 10
NORTH
CLOUOY
SF/SW
5- 10
NORTH
CLEAR
SF/SW
?i- 10
NORTH
CLEAR
SF/SW
5- 10
NORTH
CLfcAR
SF/SW
5- 10
NORTH
CLEAR
SF/SW
5- 10
NORTH
CLEAR
NW
7-12
NORTH
CLEAR
N W
7 12
NORTH
Cl 1 AK
NW
7 12
NOR 1 H
CLEAR
NW
7- 1?
NORTH
Cl FAR
NW
7-12
NORTH
Cl t AR
NW
7-12
NORTH
CLEAR
NW
.'-1?
NORTH
CLEAR
NW
7 |2
NORTH
CLLAR
NW
7- 12
NORTH
CLEAR
NW
7 12
NOR ! H
CL b AR
sc
j 10
NORIH
CLEAR
SE
5- lO
NORTH
Cl FAR
St
b 10
NOR I H
CLEAR
SF
5- IO
NORTH
CLEAR
SE
b 10
NORTH
CLEAR
5E
5- 10
NORTH
CLEAR
10
13
MAXIMUM
OPACITY
%
O
o
o
o
o
10
0
o
0
o
10
0
0
10
10
o
o
o
K1UC
COOLING
TIMF
HRrMIN
HG I
SPOTS
Y/N
COKE
DISCHARGE
LOCA 1 ION
WHARF
K1UC
K IOC
WHARF
WHARF
WHARF
WHARf-
WHARF
WHARF
WHARF
WHARF
WHARF
WHAkr
WHARF
WHARF
WHARF
KTDC
WHAMr
WHARF
Wf IARF
WHARF
WHARF
-------
QUENCHlD CCKE DISCHANGE/HANDLING EMISSIONS DATA 10:Sfc> Tuesday, March 31, 1992 1H
KRFSS, DFMONSTRATION PROJECf - BETHLEHEM STCCL CUBPORAUON
SPARROWS POINT. MARYLAND
WIND
COKF
OBSFRVLRj
W1NL
SI* CEO
OB5FRVFR
DISCHARGF
OBS
DATE
BATTEL
INITIALS WEATHER
DIRECTION MPH
LOCATION
BACKGROUND
LOCATION
397
09/06/91
1 1/1?
GW
CLtAR
SL
5 10
NORTH
CA FAR
WHARF
398
0D/0C/01
11/52
GW
CLLAK
bt
L - 10
NORTH
CLEAR
WHARF
399
08/06/91
11/12
GW
CI FAR
SE
5 10
NORTH
CLEAR
WHARF
10O
06/06/91
11/1?
GW
CLEAR
SF
5 10
NO* IH
CLEAR
WHARF
401
08/ 12/91
11/12
GW
CLEAR
Sfc
b 1b
NORTH
CLEAR
WHARF
4D2
OU/ 12/91
1 1 / 12
GW
CLEAR
SE
5- 15
NORTH
CLEAR
WHAkl
403
08/ 12/91
1 1/12
GW
Ct FAR
St
b- 1b
NORTH
CLEAR
WHARF
404
OB/ i?/n1
11/1?
GW
CLCAR
sc
5 1b
NORTH
CLEAR
WHARF
405
00/ 13/01
11/12
GW
CLEAR
SF
•1-8
NORTH
CLEAR
K IOC
406
08/13/91
1 1/12
uw
CI FAR
SF
4 8
NORTH
CLCAR
WHARF
407
08/13/91
11/12
GW
Ct FAR
SF
4-6
NOR 11 i
CLLAK
KiUC
4 08
Oft/13/fl 1
11/1?
GW
CLEAR
SL
4 8
NORTH
CI FAR
WHARF
¦109
08/13/91
11/12
GW
CLEAR
SE
4-8
NOR T H
CI FAR
WHARF
1325
1325
C
4 16
1 342
13 42
17
15
417
1 3b7
13b 7
8
10
I 1 8
I 122
1422
0
c
-------
QUENCHhD COKt DISCHARGE/HANDLING EMISSIONS OATA
KRESS DEMONSTRATION PROJECT BETHLLHIM STCCL CORPORATION
SPARROWS POINT, MARYLANO
10:56 Tuesday, March 31, 1992 20
WIND
COKE
OBSFRVERS
WIND
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DATE
BATTERY
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LCCATION
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l CC AT 1ON
•1 19
OS/' H/91
11/12
GW
OVERCAST
$E
h 10
NORTH
MAZY
WHARF
•120
Oa/19/91
11/12
(JW
OVERCAST
NW
10-15
NCRTH
CLOUDY
WHARF
42 1
08/19/91
1 1/12
GW
OVERCAST
NW
10 1 5
NORTH
CLOUDY
WHARF
422
Od/13/9 1
11/12
GW
OVERCAST
NW
10- 1 5
NORTH
CLOUDY
WHARF
12 a
oh/ia/91
1 1/ 12
cw
OVERCAST
NW
10 15
NORTH
CLOUDY
W! IARF
•12'1
oa/19/91
J 1/12
GW
OVERCAST
NW
10 15
NORTH
CLOUDY
WHARF
42b
oo/iy/yi
11/12
GW
OVERCAST
NW
i n- 1 5
NORTH
CI OUDY
WHAKf
426
08/19/9 1
1 1/12
GW
OVERCASI
NW
10-15
NORTH
CLOUDY
WHARF
•127
Od/ 19/91
1 1/ 12
GW
OVERCAST
NW
10-15
NOR Ml
Ct (JUDY
WHARF
128
03/19/91
11/12
GW
OVFRCAST
NW
10 1 b
NCR 1H
CLOUDY
WHAKf
459
08/20/91
1 1/12
GW
OVCRCAST
NW
5 10
NORTH
Ct OUDY
WHARF
430
OH/20/9 1
11/12
GW
OVERCAST
NW
5 10
NOR HI
CLUUDY
WHARF
4 3 1
oa/20/ni
1 1/ IP
C,W
OVERCAST
NW
b 10
NORTH
CLOUDY
WHARF
432
Ofl/20/9 1
11/12
GW
OVERCASI
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5- 10
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CLOUOY
WHAPf
43 J
Otl/20/9 I
11/12
CiW
OVERCAS!
NW
h U3
NCR I H
CLOUDY
WHARF
434
08/20/91
11/12
GW
OVERCAST
NW
0 10
NOR I H
ClOUDY
WHARF
4 35
oa.' 20/9 1
11/12
GW
OVERCASI
NW
5 - 10
NOR 1 H
CIOUDY
WHARF
•i jG
00/20/91
1 1/12
GW
OVERCAST
NW
fj- 10
NOR t H
CLOUDY
WHARF
437
08/20/91
11/12
GW
OVERCASI
NW
ti- K)
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WHARF
4 38
08/20/9 1
1 1/12
GW
OVERCASI
NW
5- lO
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WHARF
4 39
OH/^^/91
11/12
GW
CLEAR
SE
5 10
NORTH
Cl FAR
WHART
4 40
08/26/91
11/12
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5-10
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OHSFR
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1 1Mb
OPACITY TIME
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NUMBER
SECONDS
% HR
MIN
V/N COMMENTS
4 19
' 4 29
14 10
O
0
420
1 124
1 124
0
0
42 1
1 145
1 115
o
0
422
12 15
12 10
o
0
423
1232
1232
0
c
424
1250
1250
13
10
425
1250
1257
0
o
426
1309
1310
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0
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13 ;i
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8
15
428
1 328
1328
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429
1229
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430
1 2 S3
1253
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1257
1257
16
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432
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423
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13 18
O
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434
1335
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10
435
I 347
13-18
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436
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0
4 37
14 16
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4 38
M29
14 2H
7
1C
439
1 125
11 25
0
0
4 <10
1 145
M4h
0
0
-------
QUENCHED COKE DISCHARGL/HANDLING EMISSIONS DAI A
KKLVo Ui MUNbiNAI ION PROJtCI - tJL U ILfcH^M ST fc EL CORPORA!JON
SPARROWS POINT. MARYLAND
10:56 TuHSciny, March 31, 1992 2l
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08/26/91
1 1/ 12
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CI f-AR
SE
5 10
NOR 1 H
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WHARF
442
03/26/91
11/12
GW
CI FAR
SF
R - 1 O
NOR 1 H
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WHARF
443
08/26/91
11/12
GW
CI FAR
S£
5- 10
NORTH
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WHARF
111
08/26/91
11/12
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5-10
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WHARF
4 4 5
OS/26/91
11/12
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CLFAQ
SE
5 10
NORTH
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WHARf
446
08/26/ftt
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447
08/2G/91
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162
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-------
QUENCHED COKE DI5CHARGE/M4NDLING EMISSIONS DATA
KRtSS M-MONSIRATION PRO.If-CI - RMHll-Hf-M SHH CORPORA I ION
SPARROWS POINT. MARYLAND
10 5C Tuesday, March 31, 1992 23
OBSERVERS WIND S^FED OGSCRVER DISCHARGE
OQS
OAT £
QATTCftV
INITIAL
5 WLATHlK
DIRECTION
MPH
LOCATION
BACKGROUND
LOCATION
485
09/09/91
1 1/12
GW
CLEAR
S/SW
5 10
NORTH
WHARF
486
09/09/91
1 1/
12
GW
CI f AR
S/SW
5- IO
NORTH
WHARF
487
09/09/01
1 1/12
gw
CI FAR
S/SW
5- 10
NORTH
WHARF
488
09/10/91
1 1/ 12
GW
OVERCAST
15-20
NORTH
Ct OliDY
WHARF
489
m/10/9 1
1 1/
12
GW
OVERCAST
16-20
NORTH
CIOtJDY
WHARF
490
09/10/31
1 1/ 12
GW
OVERCAST
15 20
NORTH
CLOUOY
WHARF
49 1
09/10/91
t 1/
12
GW
OVfcRCASl
15-20
NOR 1 H
CLOUOY
WHARF
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09/10/31
11/
12
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OVfRCAS1
15 20
NOR 111
CLOUDY
Wl IARI
493
09/10/31
1 1/
12
GW
OVERCAST
1 5 - 20
NORTH
CLOUDY
WHAKh
494
09/10/31
1 1/
12
GW
OVERCAST
lb-20
NORTH
CLOUDY
WHAHh
495
09/10/91
1 1/
12
GW
OVERCAST
15-20
NORTH
CLOUDY
WIIARF
09/17/91
11/
12
GW
CLt AK
bW&NW
b- 12
NUKIH
CLbAK
WHARh
497
09/17/91
1 1/
12
GW
CL1 AR
SW&NW
o 12
NORTH
CLEAR
WHARF
4S8
09/17/31
1 1/
12
GW
CLEAR
SW&NW
6 12
NORTH
CLEAR
WHARF
4HH
oa/i//9 \
1 1/
11'
GW
CI t- AH
SWriNW
b- 12
NOR 1 H
CI bAR
WHAWF
600
09/17/91
1 1/
12
GW
C L E A ii
SW&NW
G 1 2
NORTH
CLEAR
WHARF
sot
09/17/91
1 1/
1?
GW
CI FAQ
SW&NW
6 12
NORTH
CI CAR
WHARF
bOL.-
0»/17/91
1 1/
12
GW
CLEAR
SW&NW
b - 1 2
NORIH
CLt AK
WHARh
«sr>r?
09/17/91
1 1/
1?
r,w
CI FAN
SWANW
n- 12
NORTH
CI FAf?
WHARF
504
09/17/31
1 1/
12
GW
CLEAR
SW&NW
S 12
NORTH
CLEAR
WHARF
hOf
09/17/9 1
• 1/
12
GW
Ci FAR
SW&NW
fi- 12
NORTH
CLEAR
WHARF
OOC
09/10/91
11/
12
GW
OVERCAST
sc
G 12
NORTH
CLOUDY
WHARF
OBSER
OBSER
CUMULATIVE
K I DC
VAT I ON
VArION
KPf SS
FMISSTflN MAX
imum r.noi in:;
HOT
START
FNO
BOX
T IMF OPACITY TIMF
SPOTS
OBS
TIME
"IME
NUMBER
SECONDS
% HR.MIN
Y/N COMMFNTS
4 BO
*. J J 2
1332
10
10
486
-;m?
1342
0
0
487
1357
1357
0
0
488
1 1 4G
1 14G
0
0
489
115 4
1 155
0
o
490
1228
1228
0
0
49 1
1 239
J240
0
0
402
1252
1252
0
0
493
1314
1315
0
0
494
1 3 2fl
132 8
0
o
495
1330
133G
0
0
•iyo
1 129
1 129
0
o
497
i 152
1 152
0
o
40a
1201
1201
8
10
409
1223
1223
10
io
500
12 35
1236
O
o
501
1251
1251
0
0
502
1302
1302
o
O
503
1309
13 10
10
s
504
1320
1320
0
0
BOS
1331
1331
0
0
506
1319
1319
0
0
-------
OUFNCHtD COKF DISCHARGE/hANOLING LMtbhlUNb OA I A
KRESS DEMONS i RA I i UNi PHOJLL i - BtlHLtHEM ST C E L CORPORATION
SPARROWS PlJINI, MARYLANU
tO.bb Tuesday, March 31, 1932 24
WIND
COKC
OBSERVER
S
Wi NO
SPfctU
OBSERVER
DISCHARGE*
(IBS
DATE
BATTERY
initials
WEATHER
DIRECTION
MPH
tUCA 1 TON
KACKUROliND
IOCATION
507
09/18/91
1 1/12
GW
OVERCAST
SF
6- 1?
NOR IN
01 OUDY
WHARF
5 Oh
03/10/9 1
11/12
GW
OVERCAST
St
6-12
NORTH
CI CUOY
WHARF
509
09/ 1fl/91
11/12
GW
OVERCAST
5E
6 12
NORTH
CLOUDY
W1 IARF
510
09/18/91
1 1/12
GW
OVFRCAST
SF
6-1?
NORTH
CI
WHARF
L> 1 i
09/18/91
11/12
GW
OVERCAST
SE
C 12
NCR IH
CLOUDY
WHARF
b* 2
09/ lfl/9 1
11/12
C.W
nvrsrAST
sr
b 12
NOR IH
CLOUDY
WHARF
5'3
cn/ i ft/9i
11/1?
GW
OVERCAST
5C
G 12
NORTH
CIOUDY
WHARF
bi4
co/ifl/ni
11/12
GW
OV* R(.AS 1
be
6- 12
NORTH
CLOUDY
WHARF
b 1 b
09/IB/91
11/12
GW
OVLKCA'j 1
St
G- 12
NORTH
ClOUDY
WHARF
S10
09/23/31
1 1/12
GW
UtftHCASI
sw
15 - 20
NORTH
CLOUDY
Wi (ART
5*7
09/2J/91
11/12
GW
OVERCAST
5W
15-20
NORTH
CLOUDY
WHARF
518
C9/23/91
11/1 ?
GW
OVERCAST
sw
15 2C
NORTH
Ct OUDY
WHARF
519
09/23/91
11/12
CW
OVERCAST
5W
15 20
NORTH
CLOUDY
WHARF
520
09/23/91
11/12
GW
OVERCAST
SW
* 3 l'(J
NOR iH
CLOUDY
WHARF
52 1
c
09/2-1/9 1
11/12
GW
CI FAR
FAST
10-15
NORTH
WHARF
527
09/24/0 1
11/1?
GW
CI EAR
CAST
10 15
NORTH
WHARF
528
09/24/91
11/12
GW
CLEAR
EAS1
10- lb
NORTH
WHARF
0B5Ca
ORSFR
CUMULAIlVt
KI DC
VA1:UN
VAT ION
LMISS13N MAX
1 MUM COOLING
HOT
START
END
aox
1 IMb OPACITY TIME
Cj
POTS
OB 5
TIME
TIME
NUMBER
SECONDS
'/, HR ; MI N
Y/N COMMENT
S
507
1 328
1320
0
0
5Dfi
1 336
i:kk>
10
:o
b09
134G
130 7
0
O
510
1354
1354
1 b
5
51 I
1400
1401
O
O
b 12
1111
14 12
O
0
5 13
1426
1427
0
0
b 14
5 44 1
144 1
O
10
5 15
1 45C
MSG
o
o
b 1C
1 1 2 7
1 127
0
0
5 17
' i Jo
i rj /
o
0
c If
• SJf,
1 14 f»
0
0
b If J
•• 157
1 157
0
0
s •; o
1O 7
IliOb
o
G
1
12 1G
12 1 <5
1(>
to
C22
1229
1*29
0
0
b?U
1 2 -4 3
1244
6
io
t>2 4
1253
1253
0
0
bVb
130b
1307
0
0
52C
1 1 5 1
1 15 1
10
to
557
1205
1206
0
0
5? 8
i ? 7
1? ifl
o
o
-------
OUENCHEO COKE DISCHARGE/HANDLING EMISSIONS DATA 10:56 Tuesday, March 31. 1392 2b
KRLtib UCMUNS'fiAT TON PROJFCT - RClHItHiM Slhrl CORPORA I ION
SPARROWS POINT, MARYLANO
W I N D
CGKL
ORSrQVTRS
WIND
SPFFD
onSTRVTR
CISCHARG
OBS
DATE
BAT r
ery
INITIALS WEATHER
DIRECTION
MPH
LOCATION
BACKGROUND
LOCATION
529
03/34/9 I
i 1/
i?
GW
r 1 FAR
FA^T
10- lb
NOR TH
WHARF
bao
09/24/91
1 \!
12
GW
Ct EAR
EAST
10-15
NORTH
WHARF
53 1
03/25/91
i »/
17
GW
CI tAR
EAST
IO 15
NORTH
WHARf
b32
09/25/91
1 1/
12
GW
CLEAR
EAST
10- 15
NORTH
WHARF
533
09/25/91
1 1/
1?
GW
CLEAN
LAS 1
1C - 15
NOR 1H
WHARF
L-34
Oy/^b/91
1 1/
12
GW
CLEAR
i as r
IO- lb
NORTH
WHARF
535
10/01/91
l 1
GW
CI FAR
NORTH
CLEAR
WHARF
b3G
10/O1/91
1 1
GW
CI FAR
N0R1H
CI EAR
WHARF
5.1?
10/Ot/Oi
i i
GW
CI EAR
NORTH
CLEAR
K IOC
53a
10/01/01
11
GW
Ct FAR
NORTH
CLEAR
KIDC
539
10/01/91
1 I
GW
CLEAR
NORTH
C4 FAR
KiUG
54C
1O/O2/0i
i t
GW
C L t A R
bW
b io
NOR in
Ck I AR
WHARF
5-11
10/02/91
1 I
GW
CLEAR
sw
5- 10
NOR J H
CI EAR
WHARh
54 2
10/02/91
i i
GW
C L I A R
Sw
b- IO
NORTH
CLEAR
KI DC
5 4 J
* 0/ o? / 1
1 1
GW
CLEAR
sw
b IO
NORTH
CI EAR
KIDC
-14
10/02/9 1
1 i
GW
CLEAR
sw
b- 10
NOR 1H
CLEAR
KIOC
b4b
»o/o8/y1
1 1/
12
GW
Sfc/NW
6- 12
NORTH
f I FAR
WHARF
5 IG
10/08/0 '
! 1 /
12
GW
SE/NW
fc- 2
NORTH
CI EAR
WHART
b 1 /
Ki/08/S 4.
11/
12
GW
SF/NW
S- 1?
NOR 1H
CI FAR
WHARf-
548
10/08/9i
1 1/
12
GW
SE/NW
6- 12
NORTH
CI FAR
WHARf
549
10/08/91
11/
12
GW
SE/NW
G 2
NORTH
CI EAR
KIOC
haO
10/08/9 1
1 1/
12
GW
sp/nw
6-12
NORTH
CLEAR
KIDC
UbbER
OBSER
CUPULA flVE
K1 DC
VA I ION
VATION
KRl'io
LWibblUN
MAXIMUM CUULlNvi
HOT
START
END
BOX
I IMF
OPACITY JIME
spots
OriS
T I ME
II ML
NUMBER
SECONDS
% HR:MIN
Y/N CGMMFN
S
520
1237
123H
0
0
530
1245
1245
0
0
53 1
1309
1309
0
0
532
1340
1340
0
C
533
iyjb
1 3bB
8
10
534
1406
1406
O
0
b'Jb
1 13b
1 135
O
0
536
1208
1208
7
10
537
14 1R
14 m
h?
15
2 b 0
5:38
1 54 1
154 3
123
25
3 b3
1550
IGOO
2
5 b
15
J . Ju
b40
14'Jb
14 36
fe
c;
b'l 1
14bO
14bb
o
0
b 4 2
!Cb9
1 € b 3
;j
1 f
30
b4 3
1 fc02
1802
6
2 1
35
544
1 B4t>
1817
2
3ti
55
i;4b
112 1
1 122
0
0
-46
1205
1205
0
0
54 7
1 2 1G
12 10
0
0
54 8
12 24
1224
O
0
549
1422
?
bbO
14b J
14b a
6
1 b'l
0
C PAN HNG UP
T NTFRF FRFNCF
8ALL DF F1RF
-------
OBS
S5 I
552
553
SS4
555
556
557
558
559
560
5b 1
5G2
563
504
:>6ii
566
567
563
569
570
5 7 1
57 2
ORS
551
552
553
554
555
556
557
558
S59
5 no
Fib 1
5r» ?
50 3
564
sr.s
500
5<>7
56 a
56a
'.>/<)
57 1
5 * 2
OUENCI'EO CCKL DISCHARGE/HANDLING LM1S51CN5 DAT A
K.RES5 UCM0N5 I HA ! 1 UN ffcUObCT - Bfc T HLEHtM STEEL CORPORATION
SPARROWS POINT. MARVLAND
10:56 Tu(**jiiuy. March 31. 1002 26
QKSCRVlRS
RATTFRY INITIALS
WF ATMfR
w 1 NO
DIRECTION
W1ND
SPEED
MPH
Ub-iLK'VCA!
IOCATIQN
BACKGROUND
COKr
01'jCHARGE
LOLA I ION
10/00/91
1 1/12
uw
SL/NW o-
i:»
NOK1H
CLEAR
K IDC
10/09/91
11/12
GW
CI I- AH
Sfc
5 -
10
NORTH
CI FAR
WHART
10/03/91
11/12
GW
CLEAR
SE
5-
10
NORTH
CLEAR
WHARF
10/09/91
Ii/1?
GW
CLEAR
SE
S-
iO
NORTH
Ci FAR
WHAKI
10/09/91
11/12
GW
Ci I-AR
St
5
10
NORTH
CLEAR
WHARF
IO/09/S1
11/12
G W
CLEAR
SF
5-
IO
NORTH
CLEAR
KIOC
10/09/91
11/12
GW
LI F AR
SE
*
10
NORTH
CLEAR
K IDC
10/09/91
1 V 12
GW
Ci FAR
Sb
5-
1 c
NORTH
CLEAR
Kmc
1C/09/3'
1 1/12
GW
C1 E A R
SF
h
IO
NORIM
CLLAR
KIOC
10/10/91
11/12
c.w
CI EAR
sw
4
a
NORTH
CI FAR
K IOC
10/10/91
11/12
GW
CI EAR
sw
1
a
NORTH
CLEAR
KI L)C
10/10/A 1
: • / 1 ?
GW
LLC AR
SW
4
d
N0R1H
CI EAR
KIOC
10/11/9 1
1 1
GW
C VI-RCA S I
NE
5
10
NORTH
CIOUDV
K IOC
10/11/91
1 1
GW
UVtRCAST
NE
5-
10
NORTH
Ci OUOY
KIOC
10/11/91
1 1
GW
OVFRCAST
NI-
5
\0
NORTH
CLOUOY
K IOC
10/11/91
« 1
GW
OVERCAST
NE
5
10
NORTH
ClOULJY
K1UC
10/11/91
\
GW
overcast
M
'j
10
NORTH
CLOUDY
KIOC
10/ 1 1/I 1
' \
GW
UVtkCAbl
NE
s
IO
NORTH
CLOUOY
K 3 DC
10/11/9 1
1 1
GW
OVf-RCAST
NE
5
10
NORTH
cionnv
KIOC
10/ 1 1 /L- 1
1 1
GW
OVERCAST
NE
5 -
10
NOR 1H
C4OUOY
KIOC
10/12/91
1 1
GW
CI EAR
NW
5
10
NORTH
ri far
KIOC
10/12/91
1 \
GW
CLEAR
NW
5-
10
NORTH
CLEAR
KIOC
ULiSJ R
OESER
ClJMUl AT 1VF
KI DC
vaiio\
VAT ION
KRESS
CMI5SICNI
MAXIMUM
COOL1NG
HOI
START
FNO
RCX
1 I Mk-
OH AC 1 f
T I ME
5P0 1 5
TIME
T1MF
NUMBER
SCCCNOS
%
HR:MIN
Y/N COMMENTS
151?
1533
3
02
45
1 137
1 138
14
10
120 3
1203
1 2
lO
12 18
12 10
0
1231
123 1
7
10
1 45
1501
2
C24
35
15 17
152 1
3
252
35
1 756
I 757
2
4 3
40
i 3 13
IF 1 4
3
02
J 5
1112
1112
c.
2 J
15
12 14
1^15
2
cjt
1U
1 ?4?
1- -i 2
5
4 0
•o
124
1 1 20
C
O
o
1 146
11-7
c.
0
o
12 2 5
12 2 6
If
J 1
40
HAL i_
:> i- iRt
1305
1306
3
12
10
14 JO
M31
4
1 4
5
1515
1517
5
ft
5
1555
15 5 7
2
93
35
1737
17 39
3
07
.15
1 123
1 1 2fc
5
18
10
1 155
1 157
'J
15
5
-------
QUFNCHE0 OJrft UISCMAMGC/HANOI 1NG tMISSICNS UA'A 10:56 Tuesday. March 31, ISa? 37
KRFflS DFMONSTRA f ION PROJECT - BETHI FHLM SILLL CORPORATION
SPARROWS POINT. MARYLAND
wiisii:
COKE
OhhLKVfcKb
WIND
SPEED
CBSFRVFR
Oi bCHAKtib
OR s
DATE
DAIJLKY
1 N 1 1
IMS WfcATHf-R
DIKf-CTlON
yr»H
IOCATION
BACKGROUND
LOCATION
573
10/ 1 :»/-M
1 1
r.w
C_EAR
NW
b - 10
NORTn
C Lh AK
KTOC
57 4
10/19/91
1 1
GW
clear
NW
5 10
NORTH
Cl FAR
Kinr
b'/b
10/12/01
i 1
GW
clear
NW
b - 10
NUR1H
CLEAR
KIDC
576
10/1?/91
1 1
r.w
CLCAK
HW
b 10
NOHtH
Cl EAR
KTOC
577
10/17/91
1 1
GW
ClCA*
NW
5- tO
NONIH
CLFAR
Kinr
b/U
10/12/91
1 \
uw
Cl FAR
NW
5- 10
NORTH
CLtAK
KIDC
b*/H
10/13/91
1 1
GW
CLEAR
NW
i\ i J
NOR»H
CLtAR
KIDC
560
10/13/91
1 1
GW
Clear
NW
6- 12
N0H1H
Cl fcAR
KIDC
se i
10/13/91
1 1
GW
Cl fr AR
NW
6 12
NQU tH
CL CAR
Kil>C
5P?
10/1 I/O 1
1 1
GW
CLfcAR
NW
6 12
NO R T H
C.I FAR
K i DC
5B3
10/13/91
1 1
GW
C-EAR
NW
G 12
NOR IH
Cl FAR
Kinc
5B4
10/13/91
1 1
GW
CLfcAK
NW
t; 12
NUKfh
CL r AR
KIDC
«»Rh
10/13/9 1
1 1
GW
CLEAR
NW
12
"JO R T H
CLEAR
KIDC
h8G
10/11/91
1 1
GW
CLEAR
NW
6 12
NOW 1 H
CLEAR
KIDC
bb /
•0/ 1 J.-'9 t
1 t
GW
f.v FAR
NW
6 12
NUK IH
CLfcAR
KIDC
5G8
10'14/91
11/12
GW
CA FAR
5T
5 10
NO R T H
KIDC
bB9
10/14/91
1 1/ 12
GW
CLEAR
bfc
5- 10
NOR f M
WHARF
590
10/ 4 /' 9 1
1 t./ 12
GW
CL EAR
SI
b - 1 0
NORTH
KIDC
b9 1
10/14/91
1 1/ 12
GW
Cl TAR
SE
5 10
NORTH
WHARF
bb2
10/14/91
1 1/ 12
GW
f.v FAR
SE
5- 10
NORTi i
KIDC
bSCJ
10/14/91
1 1/ 12
GW
::i f ar
c. F
5 10
NORll*
KIDC
534
10/14/91
1 1/ 12
GW
Cl FAR
SI-
h- 10
NORTH
KIDC
OR OTP
OBSCfi
CU.MULA i 1 Vt
K I IDC
VAT ION
VATION
KRESS
LMISS10N
MAX I MUM
COOL J N(»
HOT
ST AH f
l-ND
BOX
T IMC
OPACITY
T i ML
SPOl :>
OSS
TIMf-
I IMF
NiiMP.FR
srr.HNDS
0/
MR mira
Y/N COMMENIS
573
1^21*
12'JO
3
17
10
b 74
14J0
14:r.>
4
22
10
DUMP 2K
b'/b
1510
1512
5
134
20
576
17 ir
1 7 18
2
67
10
577
174 1
1 742
3
4
10
578
18 10
1812
6
2 b
10
?0 EMS
PIT
•>70
1112
J 1 1 J
4
12
b
530
1 14C
1147
b
1b
h
b8 1
12 15
1215
2
10
b
5R?
i j ?
14 13
2
49
3 5
144 1
14 4 1
u
9
5
5A4
1 b07
1509
4
\\i
b
h«n
170P
1 7 10
b
u
b
bHfe
1 7:4 J
1736
->
14
b
ba?
1 71jt
1 BOO
'A
»o
5
583
112 1
1 124
£
0
0
bao
1 146
1 149
u
0
bao
1 154
1 156
4
15
5
b91
i :> 1 7
12 18
0
0
532
1235
1237
b
10
5
593
Mil
14 13
o
19
5
594
14 38
1440
3
35
15
-------
SO
CN
3 Z
OC o
Jj < ¦—
i I h
O 3 «
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QUENCHED COKfc DISCHARGE/HANDLING ["MISSIONS DATA
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SPARROWS POINT. MARYLAND
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10/31/91
I 1/ 12
GW
CLtAR
NE
15-20
NORTH
CLEAR
693
10/31/91
11/1?
fitf
CI EAR
Nfc
15-20
NORTH
Ci FAR
by-i
IO/31/91
11/12
GW
CI f AW
Nf
15-20
NORTH
CLEAR
695
1 1/fin/9 1
11/1?
GW
01 LA*
NE
6 12
NORTH
CLEAR
696
1 1/C5/91
1 1/12
GW
CLEAR
NE
6 12
NORTH
CI FAR
697
11/Ob/31
11/12
GW
CLEAR
NE
b 12
NOH I H
CLEAR
GOB
1i/OS/31
1 1/ 12
GW
CI EAR
Nf
6-12
NOR 1 H
CI FAR
byy
1 1 ''05/91
1 1/ 12
GW
CLEAR
NL
u 12
NORTH
CL EAR
7 O D
1 1 /Ob/ *11
1 1/ 12
GW
CLEAR
Nt
6- 12
NOR 1 H
CLEAR
/01
1 1 .'05/91
1 1/12
GW
CLEAR
Nfc
S- 12
NORTH
CLEAR
702
1 1/Ob/9 1
1 1/ 12
GW
CLI AR
NE
6- 12
NORTH
CLEAR
703
1'/Ob/3 1
1 1/ 1?
GW
CLEAR
Nfc
6- 12
NORTH
CLEAR
704
1 1/06/91
1 1/ 12
GW
CLEAR
SF
G 12
NORTH
CLEAR
OBSbR
QB5FR
CUMULATIVE
K I OC
VAT ION
VATION
KRESS
EMISSION
MAXIMUM
cnnihmg
HOT
SI AH 1
END
BOX
TIME
OPACITY
TIME S
POTS
OBS
TIME
TIME
NUMB'R
SECONDS
'/
HR . MIN
Y/N COMMLN
b
09 5 1 b 10 1 b i 3 2 174 3b
604 1514 1514 . . 0
635 1521 1522 1U b
086 1523 1524 8 43 15
bH7 1b3b 1b36 0
68B 1b4l» 1U4 7 b 5
68= 15bb 1bb6 . O
090 1152 1153 2 57 15
631 1220 1223 3 113 15
692 124 1 i'243 b 60 lb
u = j 14J2 1456 2 138 30 1380 St-COlvmS
«H4 14bb J'jIO J 6*10 30
69b 120b 1206 0
bdb 1-110 14 14 8 13? 3h 2-4 I
597 14 14 mj5 0
GSR 144a 144?? 3 113 25 2:63
fcHy 1454 145c 6 4G IS 2:25
? no i 3 iB?r* a
701 1529 1529 O 0
702 153b 1536 O O
703 1544 1545 O O
704 1130 1131 0 O
COKX
DISCHARGE
IOC AT I ON
K1 DC
WHARF
WHARF
KI DC
WHARF
WHARF
WHARF
K IOC
K IDC
K IDC
K I DC
K I DC
WHARF
KIDC
WHARF
KIDC
KIDC
WHARF
WHARF
WHARF
WHARF
WHARF
-------
OKS
705
706
707
700
709
7 10
7 I I
71?
7 13
7 1 4
715
7 16
717
718
7 13
7 ?f>
7 7 1
7 ?2
7 23
724
725
12 6
OBG
70b
706
707
70ft
700
710
7 1 1
712
7 1 'J
714
7 1 b
7 IK
717
7 13
7 in
720
72 I
722
723
724
.'2b
726
QUENCMCD COKE DISCHARGE/HAN31 ING EMISSIONS OA IA 10.b6 Tuesday, March 31. 1992 33
KRESS OLMONb 1 RAT I ON PROJECT UL H ILEl ILM STEEL CORPORATION
SPARROWS P0IN1 , F4AWYLANU
WHO CUKL
OBSERVERS
WIND
SPEED
OBSERVER
DISCHARGE
UA1 E
BAT IiRY
INITIAlS
WEATHER
DI3FCTION
VPH
LGCAI|UN
BACKGROUND
LOCATION
1l/UG/91
1 \/ 12
GW
CLEAR
sc
6 12
NORTH
CLEAR
K i UC
i1/06/91
1 1/12
GW
CLEAR
SE
6 12
NURIH
CLL AH
KIDC
11/06/01
1 1/12
GW
CLEAR
St
6- 12
NORTH
Cl FAR
K1UC
i i/ufc/y1
1 1/ 12
GW
CLEAR
St
6 12
NOR IH
U FAR
KIDC
11/06/91
11/12
GW
CI FAR
SE
6-12
NORTH
CLEAR
WHARF
11/06/91
11/12
GW
Ci FAR
SE
6- J2
NOR 1 H
n FAR
WHARF
11/G7/91
11/12
GW
OVFROAST
SF
4-B
NORTH
CIOUDY
KIDC
11/07/01
1 1/ 12
OW
overcas r
SE
4 0
NORTH
CLOUDY
K IOC
11/07/91
1 1/ 12
GW
overcast
SF
4 -ti
north
CLOUDY
KIDC
1 1/07/1 1
11/12
GW
OVLIfCAb i
bt
4 n
NOR f H
C.LUUDY
KiUC
11/07/91
11/12
GW
OVFRCAST
SE
4 8
NORTH
CLOUDY
WHARF
11/07/91
11/12
uw
OVtkCAS1
SI
4 a
NOKIH
CLOUDV
WHARF
1l/OV/91
1 1/12
GW
UVhRCASI
SE
4 ti
NORTH
cinun.
KIDC
11/07/91
11/12
GW
OVERCAST
SF
4-8
NOR t H
CL OUDY
KIDC
11/12/91
1 i /1 :>
Rt A
OVT NOAS 1
NE
5-10
WFST
KIDC
11 / i :¦ / n i
11/12
pr a
HVFRCAST
NF
5-10
west
k inr
11 / 12 /»i
11/12
RLA
CVFRCAST
NF
r>-10
WEST
KIDC
11/14/91
l 1/12
RF A
c:i t aw
WEST
10
NORTH
OlJFNCH 1
KIUC
11/14/9 1
1 1 / 12
RF A
Ci FAR
WFS!
6- 10
NORTH
QUENCH T
Kinc
1 1/ 14/<1 1
1 t/ 12
RF A
CI EAR
WFST
*>- 10
NORTH
OUCNCH T
KIDC
1 1/20/01
1 S / 1 2
RE: A
CLEAR
SW
10- 15
NORTH
Cl FAR
K IOC
11/20/91
11/12
REA
CLEAR
SW
10 15
NORTH
CLEAR
KIDC
ORSFR
tMSF A
CUMUL AT IVF
K I DC
VAT TON
VAT 1CN
KRFSS
EMISSION
MAXIMUM
COOLING
HOT
Si ART
END
BOX
TIMF
OPACITY
T i ME
SPQIS
TIME
TIME
NUMBfR
SECONDS
%
MR:MIN
Y/N
COMMENTS
1 146
114 7
ft
2 6
1b
CARLE BROKE
12 18
1219
3
17
5
1428
1433
f>
264
45
3:00
14-19
1-152
3
213
45
2 : 28
1530
1531
o
0
1538
i 538
c>
0
1 135
1 136
2
0
0
1203
1204
5
43
10
1220
1 226
3
iP.
b
122b
1226
3
IB
5
I 255
1256
0
C
\ ? 10
1302
1 303
0
o
12 26
1440
1 44 1
2
f>4
K)
2 : 53
1 140
145 9
1 bO 1
5
fO
15
2.43
1151 F BALL
14 "4
14 3h
•1
45
10
3:05
1 143
145C
1457
8
2 b
IS
2 : 50
1 151
lb 12
1513
3
40
20
2 JO
1 VjJ
uno
143?
2
d
5
3 • CO
1 148
1525
$526
6
33
10
3; 10
1 151
154 7
1548
5
7
5
3 . 3b
1 1 b3
1334
1335
6
5
S
t4or*
1404
4
3
S
-------
QUFNOHI n rriKF O T V-HARC.E/HANDl i ng emissions data
KKI ss DEMONSTRATION PROJECT - BETHLEHEM STCEL CORPORATION
SPARROWS POINT, MARYLAND
Iuesday. March 31. 1992 31
WFK3
CUKK
OBSERVERS
WIND
SPFH)
OHStHVER
DISCHARGE
OBS
DATE
BATTERY
INITIAL
S WLAHItK
DIRECTION
MPH
LOCAIi UN
KACKGMOtJNO
LOCATION
727
! 1/20/01
1 1/12
RCA
CLEAR
sw
10- lb
NORTH
CLEAR
KI DC
72U
1 1/20/91
1 1/12
RL A
CLEAR
sw
ID-
NflH 1H
CLEAH
K I DC
729
1 1/20/91
1 1/12
RF A
CI FAR
sw
10- 15
NORTH
CLEAR
KIOC
730
J 1/2C/91
1 1/ 12
RFA
CLEAR
sw
10- 15
NORTH
CLtArt
K IDC
7 3 1
11/21/91
11/12
c,w
CLR/nc
sc
4 U
NOR III
OVCAST
WHARf
732
1 l/2'./9l
1 1/1?
r,w
CLR/OC
sc
1 8
NORTH
OVCAST
WHARF
733
1 1/2 1/91
1 1/12
GW
CIR/OC
St.
4-8
NORTH
OVCAST
K IDC
714
1 1/2 1/01
1 1/12
GW
CLR/OC
sc
4 H
NOR IH
OVERCAST
KIOC
735
1 1/21/91
11/12
GW
CLR/OC
St
•1 8
NORTH
nVFRCASl
K1 DC
7 IK
i 1/?1/91
11/12
GW
CLR/OC
SE
4 8
NORTH
OVERCAST
k i DC
737
1 1/2«/9l
1 1/12
GW
CIR/OC
St
4-8
NORTH
OVERCAST
WHARF
7 3 A
11/21/91
11/12
GW
CLR/OC
Sl
•1-8
NOW 1H
OVFRCAS!
WHARF
7 39
1 1 / ? 1 / H 1
1 1/12
C,W
CLR/OC
S L
10
NOR III
OVERCASI
WHARF
740
11/21/91
1 1/12
GW
CIR/OC
SF
4-8
NOR 1M
OVFRCAfiT
KIOC
74 t
i 1/2 l/9i
1 1/12
GW
CLR/OC
SC
4-8
NUHIH
OVERCAST
K I DC
74?
1 i/??/<*:
11/12
GW
GVCRCASI
SC
1 w - IS
NOR 1H
Ci OLJOY
WHARF
7 4 U
1 1 / ? ? / 91
11/12
CW
0VCRCAS1
SE
10 lb
NOR III
CLOUDY
WHARF
744
1 1/22/91
11/12
GW
OVERCAST
St
10- 1b
NOR 1H
CIQUDY
WHARF
74*
i t/72/9*
11/12
GW
OVLKCAS1
St
10 1b
NOR IH
CLOUDY
WHAflF
74K
1 1/22/91
11/12
GW
OVCPCAST
SE
10 1b
NORTH
CI OIJDY
WHARF
747
11/22/91
11/12
GW
OVERCASJ
SE
10- 1b
NOR IH
CLOUDY
WHARF
746
1 1/22/91
11/1?
GW
OVERCAST
SC
10 15
NUK III
CLOOOY
KI DC
OUSER
OK Si H
CUMULAT IVfc
KIOC
VATION
VAT ION
KKfcSS
t-Mi SSION
MAXIMUM
COO
I IMG
HOT
START
END
BOX
1 1M£
OPACI1Y
T I
Mt
SPOIS
OBS
TIME
TIME
KUM3CR
SCCONOS
%
MR:
MIN
Y/N COMMENTS
727
1420
142 1
8
8
cv
726
1 •' A 1
1447
7
12
F»
OUMP
2 X
729
lb 17
1 b3 1
1
17
10
OUMR
3X
7 JO
1 'j 'j 3
1 'j b 1
2
5
5
731
1210
124 1
0
0
12 3G
732
1 2S2
12b2
0
0
1246
v j:i
131b
1345
S
13
5
1 140
7 3-1
1407
1 107
4
q
5
1 172
7 3 b
1 4 22
112?
a
1 1
5
1 152
7 3G
1-344
' bSO
~t
a
b
11:?».»
SI ICKbW
737
1500
' 501
0
O
12 38
7 Jb
ISOH
i 'i OH
0
O
12 4b
v :) M
) S 1 7
0
0
1258
7-10
1526
16 18
1
C)
o
1 1b4
5TICKER
7 4 1
l63fi
1638
2
10
b
11/1
7 4 9
\ i 'it-.
1 156
0
0
12 2 'I
713
120B
1208
0
0
1234
STICKER
744
124 1
1 24 1
0
0
1234
12 DUMP
745
1200
i2bO
0
0
1244
746
1300
I 30O
0
0
1225
747
1332
'.332
0
0
1236
74 fc
1 34 4
6
15
5
1149
-------
QUCNCH* [) COKE f>I f,CHARGE /MANDL I NG EM.'^IONS DATA
KRESS DEMONSTRATION PROJECT BETHLEHEM STfcfcL CORPORA!ION
SPARROWS POINT. MARYLAND
1C:5G 'uesaay. March 31, iy92
WIND
COKF
OBSERVERS
WIND
SPtfcD
OBbtRVtR
DISCHARGF
035
DA ! t
BAT FfcRY
INT TIAl
fi weather
DIRECTION
MKH
llk;a i i on
BACKGROUND
LOCATION
749
1 1/22/91
* 1/
12
GW
OVERCASi
SE
10- 15
NORTH
CLCUDY
Kmc
?so
1 1 / 3 ? / 9 1
1 «/
1?
OW
0VTRCA5T
bL
10- 1b
NUKIH
CLOUDY
KIOC
751
11/22/91
11/
12
GW
OVfcRCAST
SE
10- 15
NORTH
CtOUOY
KIOC
752
1 1/22/9 1
I 1/
12
GW
OVt-KCASl
5E
10 15
NORTH
CLCUDY
K I DC
7 b.'*
1 i/??/0 *
11/
12
GW
OVERCAST
SI.
10- 15
NORTH
CLOUDY
KIOC
754
11/24/91
M/
12
GW
QVCRCAST
NW
10- 1!)
NOR 1 H
ciounv
KIOC
755
1 1/24/91
M/
12
GW
UVtKCASI
NW
10- 15
NORTH
CLOUDY
KIDC
7 5f>
1 1/24/91
I 1/
12
GW
OVERCAST
NW
10 15
NORTH
r.i nunv
KIOC
757
11/24/91
M/
12
GW
OVERCAST
Nw
10- 15
NORTH
CLOUDY
KIOC
758
1 1/24/91
< »/
\z
GW
OVCRCA'j 1
Nte
10- lb
NORTH
Cl OilDY
K1 DC
750
1 1/24/9 f
1 1/
12
GW
OVERCASI
NW
10- 15
NORTH
CI miDY
KIDC
760
1 1/25/91
M/
12
GW
CLEAR
NW
10- 1b
NORTH
Cl FAR
Kinc
76 1
1 i/?5/9 I
• 1/
1?
SBP
cl£a*
Nm
10 15
NORTH
CL EAR
KIDC
7C2
1 1/25/91
12
RJA
CLEAR
NW
10-20
NORTH
Cl FAR
KIDC
753
1 t/25/91
1 !/
!2
GW
clear
NW
JO !b
NORTH
CLEAR
KIDC
7G4
1 t/2b/9 1
1 1/
12
SBP
C ( i AR
NW
10 15
NORTH
CLEAR
KIDC
76b
1 t/2h/91
1 1/
15
R.IA
01 FAR
NW
10 20
NORTH
CLEAR
KIDC
7Gb
1 1/25/9 1
• 1/
12
GW
CI TAR
NW
10 15
NORTH
CLEAR
KIDC
767
1 l/2b/9 1
1 1/
12
r,Rp
Cl EAR
NW
10 15
NORTH
CLfcAR
KIUC
768
11/25/91
11/
12
R.JA
CLEAR
NW
10 20
NORTH
CLEAR
KIOC
7fc> y
1 1/25/91
1 1/
12
GW
CLtAK
NW
10- 15
NORTH
CLEAR
KIUC
OBSfcR
OBSER
CUMUL ATIVE
KIUC
VAT ION
VA 1 ON
krlss
LMlS'iiON
*AX1 MUM
COOLING
HOI
START
END
BOX
TIME
OPACITY
riwF
SPOTS
OB 5
TIME
T i ML
NUMBLR
btcuNus
%
HR • MIN
Y/N C0MMFNT5
749
1409
4
9
5
1 172
750
14.11
R
1J
10
1 1t>2
751
1454
7
18
20
1 135
STICKER
752
1558
2
b
5
1 1b4
751
1035
3
•At)
20
1 17 t
754
1244
1244
7
6
5
1 135
755
1345
1345
5
0
0
1 149
7bo
14 Ob
1405
G
1 2
5
1 17?
757
1 *22
1422
4
0
0
1 152
'53
1 533
1503
2
o
0
i 154
759
1 -,'.8
i55n
1
S'1
25
2 5 7
» I4BF I RFF5M I
7GC
1255
1255
1
23
h
117 1
.'(» !
1 255
I 2 ' > .
7
t>
1 1 7 1
7H?
1 ?55
1
7
2 b
b
1 1 7 1 LGOKGOOD
763
•35 1
135 f
5
1 f
5
1 14.4
764
35 1
1.35 1
b
1b
5
1 149
76"j
115 i
1 35 i
5
1 'j
b
1 1 4 9 LUOKGOGO
7GG
1413
14 13
6
5
5
1 172
767
14 13
14 !3
G
O
0
1 172
?«a
1413
14 13
6
O
0
1 172LOOKGOOD
763
1429
1429
4
0
0
1 152
-------
QUENCHED COKE O! SCHARGE/HANDL i NG fcMlSSlONS DA I A 1G . bfe luestla/, March 5 1 . 199? 36
KRESS DEMONSTRATION PROJECT BETHLEHEM STEEI CORPORATION
SPARROWS POINT. MARYLAND
UBS
770
111
DA It
11/25/91
I 1/25/01
BATTERY
11/1?
M/ 12
ORSFRVFRS
INITIALS
GW
GW
WEATHER
CLEAR
CLEAR
WIND
DIRECTION
NW
NW
W I MO
SPECD
MPM
10 * 5
10- Vj
cybfcwvt«
LOCATION
NCRTli
NUK IH
BACKGROUND
CL CAR
CLEAR
COKE
DISCHARGE
LOCATION
KIDC
KIUC
OBS
no
7 7 1
OBSER
VAT ION
START
TIME
1452
1532
OBSER
VAI ION
FND
TIME
1502
15J2
Kwess
POX
NUMBER
8
2
CIJMUL ATIVF
EMISSION
TTMF
SECONDS
17
O
MAXIMUM
OPACiIV
K
K I DC
COOLING
TIME
HR M1N
H0~
SPOTS
Y/\
COMMENTS
1 1 J5 UI'tiCQrft'
1 i 5-3
tD
I
\o
Ul
-------
Section 7
Emission Statistics T-test Results
B-96
-------
AVERAGE MAXIMUM OPACITY - KIDC VS CONVENTIONAL
COKE OVEN TOPSIDE OBSERVATIONS
14:43 Hi day. July 10. 1992
T T C ST PROCFDIJRf
VarlODl©: MAXOP
PECS N
jtd brror
CONV
KIDC
3 12
97
4 ! 14743590
30 . 4639 1 753
33.47550560
25.3935941\
1 .80513185
2.57832804
0.OOOOOF +00
2.OOOOOE *01
Ma x tmum
100.OOOOOOOO
100 oooooooo
Vnr i aru:i;i.;
Unequal
Ei|ua 1
10.4117
-9.0250
208 9
40/ U
Prob>|Tj
O.OOO1
0-0000
For HO: Variances are equal, F' * 1.74
DF
(31 t, 96 )
Prob>F ' = 0 0017
AVERAGE MAXIMUM OPAClIY - II BA1 I . VS. 12 UA! 1 .
COKfc OVfcN IQPSIUfc OBSERVATIONS - CONVENTIONAL PUSHES ONLY
14 4 3 fnday, Uu 1 y 10.
TTEST PROCEDURE
variable: maxuh
OVNO N
Std Dev
Std Error
Mint mum
1 100
1200
68
244
5 I 02941176
46.06557377
35 25555766
32.95607195
4 27536436
2.10979631
Max imum
too OOOOOOOO
100.OOOOOOOO
varlances
DF
Prot>> j T |
UnequaI
Eqja 1
1 04 12
1 00 1G
101 .9
310.0
0 3003
0 2803
For HO: Variances are equal. F'
(67.243>
0.4620
HUSHfcK SIDE OVLN EMISSIONS AND TIME OF EMISSIONS T I LSI
KIDC VS. ALL CONVENT TONAI PUSHES
MAXIMUM OPACITY (MAXOP )
CUMUtATIVF riMfc Oh EMISSIONS (CTDE)
15:06 Friday, July 10, 1992
TIE ST PROCEDURE
Variable- MAXOP
ECHN N
CONV
KIDC
283
126
Std Oev
51 39575972
61.90476190
32 7235 1806
35 93247636
Std Error
Mini mum
Max irnum
1 *452 1124
3.20111942
5 OOOOOOOO
10.OOOOOOOO
100.OOOOOOOO
100.OOOOOOOO
Var tances
Unequa1
Equal
OF
-? 8055
2.908 1
221 O
407 .0
O OObb
0.0038
For HO. Variances are equal.
(125.282)
Prob>F' - 0.20C'j
Variable: CTDE
LCON N Mean Std Dev Std Error Minimum Maximum Variances T DF Prob>|lj
CONV 283 57.35335689 23.55081357 1.75661353 b.OOOOOOOO 165.00000000 Unequal -0.6203 322.4 O.bJbb
KIDC 125 58 96000000 21.27788493 1.90315188 5.00000000 109.OOOOOOOO Equal -0.5482 40G.0 0 5839
For HO: Variances are equal, F' = 1.93 DF - (282,124)
Prob>F' - 0.0000
-------
PUSHER SIDE OVFN EMISSIONS AM) TIME OF EMISSIONS T TEST
KIDC V5 CHEM1CO PUSHES
MAXIMUM OPACITY (MAXOP)
CUMULATIVE TIME OF EMISSIONS (CfOF)
15: Of* Friday, %luly 10, 1992 2
T TEST PROCEDURE
Variable: MAXOP
ECON N
CHFMICO
KIDC
58
126
4!> .G8b20630
6 1.90476 190
For HO: Variances are tiqual.
33.43013157
35.93247636
Std Error
4.39037916
3.20111942
( 125,57)
5.OOOGOQOO
10 OOOOOOOO
lOO.OOOOCGOO
100.OOOOOOOO
Viir i arces
unequal
tqua1
-3.0954
3 0138
OF Prob>|T j
1 1ft 4
182 O
O.OG2b
O.OQ29
Variable: CTOE
ECON N Mean Std Dev Std Error Minimum Maximum Var lances T OF Pit>h>|T|
CHEMICO 5B 57.68965517 26 12668656 3.43060202 5.00000000 95.OOOOOOOO Unequal 0.3238 93.4 0.7468
KIDC 125 38 9G000000 21 277B8493 1 90315188 5.OOOOOOOO 109.OOOOOOOO Equal -0.3489 181.0 O 7276
Tor HO: Variances are equal, f' = 1.51 OF - (b7,l24) Prob>F' 3 0.0604
PUSHER SIDE OVEN EMISSIONS AND TIME OF EMISSIONS T TEST
KIDC VS. SHENANGO PUSHES
MAXIMUM OPACITY (MAXOP)
CIJMU1ATIVF T IMF OF FMISSIONS fCFOfcl
15:06 Friday, July 10, 1992 3
TTFST PROCEDURE
Var labl c •
ECON
Std Dev
Std Error
Max ilium
KIDC
SHENANGO
126
225
6 1 90476 190
53.02222222
35 93247636
32 41368269
3 20111942
2 16091218
10 OOOOOOOO lOO OOOOOOOO
5 OOOOOOOO 100.OOOOOOOO
Var iances
Unequa1
Equa I
2.2999
2.3677
OF
237 . 4
349.0
P rGt» | I j
O.G223
0.0184
For HO; Variances are equal, F'
1 .23
DF = ( 125,224 )
f»rot>>F
0.1834
Var (able: CTOE
ECDN N Mean Std Dev Std Error Minimum Maximum Variances T DF Prob>|T|
KIDC 125 58.9SOOOOOO 21 277B8493 1 90315188 500000000 109 00000000 Unequal 0.6088 330.0 0 5431
SHENANGO 225 57.26666667 30.42408585 2.02827239 5.00000000 165.00000000 Equal 0.5517 348.0 0.5815
For HO: Variances are equal, F' - 2 04 DF = (224,124) Prob>F* = O 0000
-------
PUSHER SIDE OVEN EMISSIONS AND TIMC GT EMISSIONS T TFST 15.06 Friday, duly 10. 1992 4
11 BATTERY VS. 12 BAIifcRY
MAXIMUM OPACITY (MAXOP)
CUMULATIVE 1 IMF OF EMISSIONS (CIOE)
TTFST PROCEDURE
variable; MAXOP
OVEN N Mean Std Dev Std Lrror Minimum Maximum Variances T OF Prob>|l|
1100 9Q 52.83333333 33.912O6408 3.57464542 5.00000000 100.UOOOOUOO Unequal 0.4947 166.1 O.C215
1200 193 50.72538860 32.22224626 2.31940804 5.00000000 100 - OOOOOOOO fcqual O.iKMO 281.0 0-6147
For MO: variances are equal. F' « 1.11 DF = (89,192) Prot»F* ¦ 0.5564
Variable: CTOE
OVEN N
Mean
1100
1200
90
193
Std Oev
Std Error
M1n imum
Max?mum
58.22222222
56 94818653
25.98304450
3 1 . 13072921
For HO* Variances are equal. F'
2.73885337
2.24083892
DF ¦ (192.89)
10 OOOOOOOO
5 OOOOOOOO
126.00000000
165 OOOOOOOO
Var i ances
Unequal
Cqua I
OF Prob>|T|
O.3600
0.3372
205 4
28 1 .0
0 7 192
0-7362
Proo>f'
0.0548
W
I
\Q
QUENCHED COKE DISCHARGE/HANDLING EMISSIONS X
KI DC VS. WHARI- DI SCHARGt
f T EST PROCEDURE
Variable*- MAXOP
LOC N
Mean
K1DC
WHARF
167
584
13.47305389
1 .64897260
12.84*120753
4 02629423
15:12 Fi Iday, July 1Q, 1992
Stil Frror
Mini murr.
O.99391462
0.16660924
Maximum
Variances
DF
Prob>|T|
0 GO-OOOOOOOO
o 20.OOOOOOOO
Unequa1
Equal
1 1 .7328
19.2138
175.4
749 .0
0.0001
0 0000
For HO: Variances nro equal, F
10 16 DF ¦ (166.583) Prob>F' ^ O 0000
-------
Appendix C
Keystone Environmental Resources Report on
KIDC Box Gas Sampling
-------
BETHLEHEM STEEL CORPORATION
SPARROWS POINT, MO
DETERMINATION OF CONCENTRATIONS
OF VOLATILE AND SEMI-VOLATILE
ORGANIC COMPOUNDS IN THE HEADSPACE
OF KRESS BOX #3
Prepared fori
BETHLEHEM STEEL CORPORATION
BETHLEHEM, PA
Prepared by:
KEYSTONE ENVIRONMENTAL RESOURCES, INC.
3000 TECH CENTER DRIVE
MONROEVILLE, PA 15146
PROJECT NUMBERS 395110-01
MARCH 1992
-------
TABLE OF CONTENTS
1.0 INTRODUCTION
2.0 METHODOLOGIES
2.1 Volatile Organic Compounds
2.2 Polynuclear Aromatic Hydrocarbons...
2.3 Phenols and Cresols
2.4 Phthalates
3.0 RESULTS
4,0 RECOMMENDATIONS
Page
1-1
2-1
2-1
2-2
2-2
2-3
3-1
4-1
LIST OF TABLES
TABLE 1-1 Test Program Target Compounds
TABLE 3-1 Volatile Organic Compound Data
TABLE 3-2 Scan of Volatile Organic Compounds
TABLE 3-3 Polynuclear Aromatic Hydrocarbon Data
TABLE 3-4 GC/MS Scan of Polynuclear Aromatic Hydrocarbons
Compounds
TABLE 3-5 Phenols and Cresols Data
TABLE 3-6 GC/MS Scan of Phenols, Cresols, and Other Compounds
TABLE 3-7 Phthalates Data
TABLE 3-8 Gas Characteristics
and
... 1-la
... 3-2a
...3-2b
...,3-2c
Other
... 3-2d
... 3-2e
....3-2f
-,..3-2;
...3-2!
APPENDICES
APPENDIX A FIELD DATA SHEETS
APPENDIX B ANALYTICAL RESULTS
APPENDIX C EMISSIONS CALCULATIONS
Dtihlehem Seed 39511941 3/92
DRAFT
r-i
-------
t.0 INTRODUCTION
On October 30, 1991, a diagnostic test program was conducted on Kress Box #3 at the
Bethlehem Steel Corporation (BSC) Sparrows Point, Maryland plant. The Kress Box is
designed to virtually eliminate quenching emissions by cooling the coke using a process
called indirect dry cooling. After the hot coke is loaded into the Kress Box, the box is
sealed and taken to the quenching area where a large volume of water is poured over ;t,
whereby indirectly cooling the coke contained inside. The purpose of the testing was to
determine concentrations of volatile organic compounds (VOC's) and semi-volatile organic
compounds (SVOC's) in the head space of the Kress Box during the indirect cooling
process. . Semi-volatile organic compound groups include potynuclear aromatic
hydrocarbons (PAH's), phenols and cresols, and phthalates. Table 1-1 presents a detailed
listing of the VOC's and SVOC's that were targeted in this test program. Three tests were
conducted for each of the two constituent groups. The sampling took place at
approximately five minutes and at two hours following the loading of the freshly pui'-fd
coke into the Kress Box #3.
Sample collection was performed by the Air Quality Engineering Division of Keystone
Environmental Resources, Inc., Monroeville, Pennsylvania. The test crew was comprised
of Mark Grunebach, Manager of Monitoring Services, Patrick Stockton, and Thomas
Morgan. Testing was coordinated by George Ossman of Bethlehem Steel Corporation,
DtlhlehemS:ecl MSIC-OI 3/72
l-l
C-4
-------
TABLE 1-1
BETHLEHEM STEEL CORPORATION
SPARROWS POINT, MD
KRESS BOX #3
TEST PROGRAM TARGET COMPOUNDS
Volatile Organic Compwfo
acrylonitrile
benzene
chloroform
2,4-dinitrptoluene
2,6-dinitroto!uene
ethyl benzene
isophorone
styrene
toluene
m/p xylene
o-xylene
Semi-Volatile Organic Compounds
(Polvnuclear Aromatic Hydrocarbons')
acenaphthene
acenaphthylene
anthracene
benzofalanthracene
benzo(a)pyrene
benzo{V)tluoranthene
benzo(k)fluoranthene
benzo(g,h,i)perylene
carbazole
chrysene
dibenzo(a,h)anthracene
fluoranthene
fluorene
indeno(l,2,3-c,d)pyrene
naphthalene
phenanthrene
pyrene
Semi-Volatile Organic Compounds
('Phenols and Cresols^
2,4-dimethy!phenoi
4,6-dinitro-o-cresol
parachlorometacresol
pentachlorophenol
her.ol
pne
2,4,
6-trichlorophenol
Semi-Volatile Organic Compounds
(Plnhalatw)
bis(2-ethy[hexvl)phthalate
butyl benzyl phthalate
di-n-hutyl phthalate
di-n-octyl phthalate
diethyl phthalate
dimethyl phthalate
Bethlehem Ste«| Corporation 355110-01 3/92
¦la
DRAFT
r-5
-------
2.0 METHODOLOGIES
The following EPA test methodologies were used in the test program: modified EPA
Method TO-l for VOC, modified EPA Method 5 for PAH, modified EPA Method TO-8
for phenols and cresols, and modified EPA Method 5 for phthalates. The specifics for each
test and analytical methodology are discussed in the following sections.
2.1 Volatile Organic Compounds
Volatile organic compounds were determined with a modified EPA Method TO-l set up.
The standard Method TO-l configuration requires a 1 to 2 gram portion of Tenax
adsorbent resin. The apparatus was modified such that the stainless steel sorbent cartridge
contained approximately 2 grams of charcoal followed by 2 grams of Tenax resin; the
charco.! and Tenax were separated by a plug of glass wool. Three test runs were
conducted tV the determination of VOC's. The first test run utilized only one M.rb;nt
car 4ge, while the second and third test runs employed two sorbent cartridges arranged in
series; the cartridges are identified as the primary cartridge and the secondary cartridge.
The dual cartridge arrangement used for the second and third test runs was employed to
determine any breakthrough from the primary to the secondary cartridge.
Analysis was performed by thermally desorbing the collected constituents into a
cryofocusing trap. The sorbent cartridge contents were then analyzed by gas
chromatography (GC) with ion trap detection (ITD). For the first test run, the constituent
VOC's were not quantified. Rather, a scan of the collected constituents was performed to
identify the most prominent VOC's collected. For the second ana third test runs, both
primary and secondary cartridges were analyzed and quantified separately for the
constituents listed in Table 1-1. An identification scan was also performed on the
adsorbent cartridges from the second and third tests.
2.2 Polynuclear Aromatic Hydrocarbons
Polynuclear aromatic hydrocarbons were determined utilizing a modified EPA Method 5
sample train. Modifications pertained to the bacic half of the sample train such that two
XAD-2 adsorption canisters, arranged in series, replaced the first three Method 5
B«ilileh«m Sk«1 395110-01 3/91
2-1
jf)D ,4\rT
-------
impingers. The adsorption canisters are identified as the primary canister and the
secondary canister. An impinger containing silica gel followed the two XAD-2 canisters to
collect any remaining moisture. The dual XAD-2 canister arrangement was used to
determine any breakthrough from the primary to the secondary canister. For the first test
run, only the resin of the primary XAD-2 canister was prepared for analysis. The resin was
extracted in a Soxhlet extractor using methylene chloride and submitted for analysis by gas
chromatography/mass spectrometry (GC/MS) in accordance with EPA Method 8270. This
sample was scanned for the twenty most prominent compounds and was also quantified to
identify the specific PAH compounds listed in Table 1-1, For the second and third test
runs, the primary and secondary canisters resins were extracted separately with methylene
chloride in a Soxhlet extraction apparatus and concentrated to known volumes. These
extracts were submitted for high performance liquid chromatography (HPLC) analysis in
accordance with EPA Method 610.
23 Phenols and Cresols
Phenols and cresols were determined using a modified EPA Method TO-8 sampling
apparatus. Modifications to the sampling train set up included the addition of a filter prior
to the impingers and the use of three Greenburg-Smith impingers in place of two midget
impingers required by the method. The purpose of the filter was to screen out particulate
matter that may have normally been entrained in the impingers, The filter was not
analyzed for phenols and cresols. All three impingers contained 100 mL each of 0,1 N
NaOH. The third impinger was added to determine if any breakthrough occurred from the
first two impingers to the third impinger. The first two impinger solutions of the first test
run were combined and extracted. The extract was scanned for the twenty most prominent
compounds using GC/MS. The third impinger solution from the first test run was not
analyzed. From the second and third test runs, the first two impinger solutions were
combined and extracted while the third impinger solution from each test was extracted
separately. All extractions were performed with methylene chloride. The extracts from the
second and third test runs were then analyzed using GC/MS in accordance with EPA
Method 8270.
BcthlclKm Steel 395110-01 3/92 2-2
r-7
-------
2.4 Phthalates
Phthalates were determined using a modified Method 5 sampling apparatus. Modifications
pertained to the impinger contents and clean up of the sampling train. The first three
impingers contained 100 mL each of deionized distilled water. The third impinger whs
added to determine if any carryover had occurred from the first two impingers to the third
impinger. Methylene chloride was used to rinse all sample train components during field
clean up. All sample extractions including sample train filter digestion were performed
with methylene chloride. The first two impinger solutions and the sample train filter of the
first test run were combined and extracted. The extract was scanned, but not quantified,
for the twenty most prominent compounds using GC/MS. The third impinger solution
from the fust test run was not analyzed. For the second and third test runs, the first two
impinger solutions and sample train filter were combined and extracted while the third
impinger solution from each test was extracted separately. The extracts for the second and
third test runs were submitted for GC/MS analysis in accordance with EPA Method 8270.
2.5 Gas Characteristics
During the test runs for PAH's and Phenols and Cresols, measurements were taken for
percent O2, percent combustible gases, and static pressure of the Kress box. Percent O?
and percent combustible gases were measured using a Teledyne Analytical Instruments
Model 980 Portable O2 / Combustible Gas Analyzer.
Btihlehem Sieel 39JUC-01 3/92
2-3
-------
3.0 RESULTS
Tables 3-1, 3-3, 3-5, and 3-7 present concentrations of the different chemical compounds
for the VOC's and SVOC's group. The concentrations of the various compounds are in
units of parts per billion by volume (ppb) and grains per dry cubic feet (gr/dcf) or grains
per dry standard cubic feet (gr/dscf). The concentration for the various compounds are
presented for each sample train portion (primary and secondary churcoal/tenax sorbent
cartridges, primary and secondary XAD-2 cartridges, and impingers I and 2, and impinger
3), Collection efficiencies for the different adsorption/absorption systems are shown in
these tables. Many of the concentrations were found to be below detectable limits, thus, no
collection-efficiency information is provided in these cases. With regard to the detectable
quantities of VOC's, the sorbent system exhibited a collection efficiency of 100 percent.
The collection efficiency of the PAH sorbent system was generally greater than 90 percent.
There were sue instances where the collection efficiency fell below 90 percent. The
impinger absorption system for the detectable phenols and cresols showed a collection
efficiency of 95 percent or greater. All phthalate concentrations were below detectable
limits, thus no collection efficiency determinations could be made, Other related testing
parameters are also presented in these tables such as sampling port temperature (°F), start
and finish times, sampling time duration, and gas sample volume in the units of dry cubic
feet (def) or dry standard cubic feet (dscf).
Tables 3-2, 3-4, and 3-6 summarize the results of the test sample scans for the different
compound groups. The objective of the scans was to determine the twenty most prominent
compounds collected by each media. Table 3-2 lists the VOC's detected during the s ^
the three test run samples. Table 3-4 lists the PAH's and other compounds dete*.
sample submitted for GC/MS analysis. The Table 3-6 lists the phenols, cresols, and
compounds that were identified in the sample scan. In Tables 3-4 anU mknown
hydrocarbons were detected in the scans. The analytical equipment, due to the absence of
gas standards and retention time information, was unable to discern the specific ty, ; of
hydrocarbon. The compounds were assigned to the hydrocarbon group that most closely
resembled that particular compound. The compound was designated as an aliphatic
hydrocarbon, an aromatic hydrocarbon, or simply a hydrocarbon. Table 3-6 shows two
compounds, CtJlio Substituent Methyl and C3 Substituent Phenol. The analytical
equipment, once again, was unable to determine the exact type of compound. The CuHjo
Delhlehem Suet 3551104)1 3/92
3-1
-------
Substituent Methyl compound lias a methyl base with an attached CuHjq molecule.
Similarly, the Cj Substituent Phenol compound is comprised of a Phenol base with three
carbon atoms attached. Each of these two substituent-type compounds can be constructed
in several different ways, consequently the specific name of the compound is unknown.
With regard to the phthalate compounds, a GC/MS scan was performed on solutions of
impingers 1 and 2 for the first test run, however, there were no phthalate compounds or
other compounds detected in the sample. The results of this scan is consistent with the
quantification analysis performed on test runs 2 and 3, as shown in Table 3-7. Test runs 2
and 3 concentrations were all below detectable limits.
Table 3-8, summarizes measurements for percent O^, percent combustible gases, and static
pressure taken during four test runs. Percent O2 ranged from 0.5 percent to 1.4 percent.
Combustible gases were measured at greater than 5 percent for all test runs. All
measurements are shown to be greater than 5 percent because the combustible gas
analyzer can only indicate concentrations up to 5 percent. Thus, concentrations that
surpassed this upper limit of 5 percent on the meter %vere simply designated as greater than
5 percent. The static pressure of the Kress box ranged from -0,1 to -0.3 inches of water.
Bethlehem S*cl 395U0-O: 3/92
3-2
C-10
-------
TABLE 3-1
BETHLEHEM STEEL CORPORATION
SPARROWS POINT, MD
KRESS BOX 13
VOLATILE ORGANIC COMPOUND DATA
Kin 2
BS-VOC-2
10/30/91
Pruiuury
Sorbet*
Cartridge
Secondary
Sorter*
Cartridge
Total
Percent
Collectiaa
Efficiency
(*)
CONCENTRATIONS
Acrylooilrde
(PTk>
<
¦ 1 52
<
! .52
<
3.04
ter/D-F>
<
1.43E-06
<
1.43E46
<
2.J7E-06
CNBD
Bctuoie
(Pt*)
<
1 03
<
I 03
<
2-06
<
1 43E-06
<
1 43E06
<
2 &7E 06
CNBD
2,4 Diniiiotuiueec
<
0 44
<
0.44
<
0 s»
Cgr/DCD
<
1 43E-C6
<
1.43E-06
<
2.87E-06
CNBD
2,6- OiniiTiHtiiueRc
Cl1*>>
<
0 44
<
044
<
0.88
(gr/DCF)
<
I.43E06
<
I.43E-06
<
2 &7E-06
CNBD
ESihyt Ben^coc
(ft*')
0.92
2.53
3.45
C^i/DCF)
I.74E-06
4.79E-06
6.S3E-06
CNBD
l*r>horooe
(Pf*>)
<
05S
<
0.58
<
1 16
(Sr/DCf)
<
1.43E-06
<
1 43E-06
<
2 S7E-06
CNBD
Styicnc
<
0.77
<
0.77
<
1.54
:Af'DCF)
<
I 43E-06
<
I.43E-Q6
<
2 87E06
CNBD
Tolucac
<
0 87
<
0 87
<
1.74
(>,i/DCF)
<
1.43E-06
<
I.43E-06
<
2.87E-06
CNDD
M>P-Xykrx
£ppb)
<
0.76
0 83
1.59
(ir'
ta.nplifig Tirac .inuto) IS
ample Volume .UCF) 0.107S
Ni*c&:
CNBD — Can No* Be Determined
Percent Ccllecttoa ELTicency = (l-Sttaaduy/Priiiuy)4]OQ
ppb — p«ns per fcUJio* by vcl» •
Cu.iccntislkxtf expressed in (. yCF cao aot he ionvettcd le> Oandard ccmfcticxis because of lack of accessary dots.
Rn 3
BS-VOC-3
1C/3CW91
Pi unary
bccundary
Kfeiccal
Soifceot
&ort>ent
Collection
Cartridge
Cartridge
Tool
Eflkincy
. _.
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<
28
<
I.35E-06
<
I.35E-06
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CNBD
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1.0
118 9
s
119.9
<
I.35E-06
I.66E-04
*;
167K-04
CNBD
<
0.6
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0.6
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1.2
<
1 35K-06
<
1 35E4J6
<
2.71 E-06
CNBD
60.9
<
04
61 3
1.98C-04
<
1.3SE-C6
£
1.99E-04
100
<
0.4
<
0.4
<
0 8
<
I.35E06
<
1.35E-06
<
2.71E-06
CNBD
1.6
<
0.7
2.3
2.93E-06
<
1.35E-06
£
4.29E-06
too
<
0.5
<
0 5
<
I
<
1.35E06
<
1 35E-06
<
2 71E -06
CNBD
<
0.7
<
0.7
<
14
<
1 35E-06
<
1.3SE 06
<
2.71E-06
CNBD
<
0.8
<
0.8
<
1.6
<
I.35E-06
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CNBD
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SO
16:46
17:01
15
C. I i 3$
V-'.
: ' ¦ t
-------
TABLE 3-2
BETHLEHEM STEEL CORPORATION
SPARROWS POINT, MD
KRESS BOX m
GC/TTD SCAN FOR VOLATILE ORGANIC COMPOUNDS
Test Sorbent Volatile Organic Compounds
Number Cartridge _
BS-VOC-1 Single l,i-Dibromo-2-Chloro-2-F!uro-Cyclopropane
Carbon Monoxide
BS-VOC-2 Primary Ethyl Benzene
Secondary Ethyl Benzene
M/P-Xylene
BS-VOC-3 Primary 2,4-Dinitrotoluene
2-{2-(Ethenyloxy)Ethonxy]-Ethanol
Ethyl Benzene
M/P-Xylene
Secondary 2,4-Imidazolidinedione
n-Methyl-i -Octanamine
Carbon Monoxide
Benzene
1,3-Dioxolane-2-Methanol
1, l-Oxybis[2-Ethoxy]-Ethane
Thieno[3,2-C]Pyridine
draft
Notes:
Test Run H\ used only one charcoal/tenax sorbent cartridge in its sampling train.
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-------
TABLE 3-4
BETHLEHEM STEEL CORPORATION
SPARROWS POINT, MD
KRESS BOX #3
GC/MS SCAN FOR POLYNUCLEAR AROMATIC HYDROCARBONS
AND OTHER COMPOUNDS
Test XAD-2 Polynuclear Aromatic Hydrocarbon Compounds Chemical Compound
Number Cartridge and Other Compounds ____ Category
BS-PAH-1 Primary Acenaphthene PAH
Acenaphthylene PAH
Anthracene PAH
Benzo(a)anthracene PAH
Benzo(b)fluoranthene APH
Benzo(k)fluoranthene PAH
Ben2o(g,h,i)perylene PAH
Benzo(a)pyrcnc PAH
Benzothiophene PAH
Carbazole PAH
Chrysene PAH
Dibenzo(R,h)anthracene PAH
Dibenzofuran AH
Dimethylnaphthalene PAH
Dimethylph.enol PC
Fluoranthene PAH
Fluorene PAH
IH-lndene PAH
Indenol(i,2,3-cd)pyrene PAH
Methylnaphthalene PAH
Methylphenol PC
Naphthalene PAH
Phenanthrene PAH
Phenol PC
Pyrene PAH
Styrene VOC
Thiophene AH
Unknown Aliphatic Hydrocarbon
Unknown Aromatic Hydrocarbon
Unknown Hydrocarbons
Notes:
For Test Run Hi, only the primary XAD-2 cartridge was submitted for GC/MS scan.
PAH = Polynuclear Aromatic Hydrocarbon
AH = Aromatic Hydrocarbon
PC = Phenol/Cresol
VOC = Volatile Organic Compound
*
-------
TABLE 3-5
BETHLEHEM STEEL CORPORATION
SPARROWS POINT, Ml>
KJCESS BOX #3
PHENOLS AND CRESOLS DATA
BS PHCR-2 BS-PHCR-3
10/30/91 10/30/91
Percent Percent
impiogen
I & 2
Impmger
3
Total
Collect! oo
Efficiency
(«)
Impinge rs
1 &2
[mpinger
3
T«W
Collection
Efficiency
<*)
CONCENTRATIONS
2,4-DimethyIpbenoI
(gr/DSCF)
<
7.44E 05
<
8.39E-06
<
8.27E-G5
CNBD
I.83E-04
8.49E-06
L92E-04
95.4
4,6 Dimtro-o-cresol
(gr/DSCF)
<
3.72E-04
<
4.19E-05
<
4.14E-04
CNBD
<
! I4fi- 105 80
SAMPLING CONDITIONS
Teat limes Sun 14:38 16:42
Fmisk 15:C8 17:12
Sampling, Time (minutes) 30 30
Sample Volume (DSCF} 15.668 11.945
Notes;
CNli / - Can Not Be Determined
PiiiCollection Efficiency (l-lmpwger 3 / Impmgers 1 Sc. 2)*10Q
*-%!»*»,. .ft
U^PiT I
-------
TABLE 3-6
BETHLEHEM STEEL CORPORATION
SPARROWS POINT, MD
KRESS BOX #3
GC/MS SCAN FOR PHENOLS, CRESOLS, AND OTHER COMPOUNDS
Test
Number
Impingers Phenols, Crcsols and Other Compounds
BS-PHCR-1 1 8c 2
Benzonitrile
Benzothiophe.ne
Dibcnzothiophene
Dimethylnaphthalene
Ethylphenol
IH-Indene
Isoquinoline
Methyldibenzofuran
Methylnaphthalene
C14H10 Substituant Methyl
C3 Substituant Phenol
Trimethylphenol
Unknown Aliphatic Hydrocarbon
r
Notes:
For Test Run #1, only solutions for impingers 1 and 2 were submitted for GC/hr'
6
-------
TABLE 3-7
BETHLEHEM STEEL CORPORATION
SPARROWS POINT, Ml)
KRESS BOX »
PHTHAI-ATES DATA
BS-PHT-2
10/30/91
Percent
Collect! oo
impiagers
Impingers
Total
Efficiency
1 &2
.. .
3
_<*>
CONCENTRATIONS
Bis (2^ethylhexyl} PhthaUte (gr/DSCF)
<
7.13E-06
<
8.9IE-09
<
7.14E-06
CNBD
<
Butyl Benzyl Phtlulaie
(fir/DSCF)
<
7.13E-06
<
8.91 £-09
<
7.14E-06
CNBD
<
Di ii- Butyl PhthaUte
(gr/DSCF)
<
7.13E-06
<
8.91 B 09
<
7.14E 06
CNBD
<
Di n Octyl Phthalate
(gt/DSCh)
<
7.13E-06
<
8.91E-09
<
7.14E-06
CNBD
<
Diethyl Phthabte
(gr/DSCF)
<
7.13E-06
<
8 91E-09
<
7.14E-06
CNBD
<
Dimethyl Phthalate
(£r/DSCF)
<
7.13E-06
<
8.9IE-09
<
7.14E-06
CNBD
<
SAMPLING PORT CONDITIONS
Tcrcperature (°F) 10?
SAMPLING nOKDlTIONS
Test limes Suit 14:38
Finish 15:08
Sampling Time (minutes) 30
Sample Volume (DSCF) 17.293
Nulcs:
CNBD - Can Not Be Determined
Percent Collection Efficiency - <1 - Impinger 3 / Impingers 1 & 2)* 100
BS-PHT-3
10/30/91
Percent
Impiogcrt
1 &2
Impingers
3
Tool
Collection
Efficiency
(*>
8.46E-06
<
S.29E-09
<
8.46E-0O
CNBD
8.46F.-06
<
5.29E-09
<
8.46E-06
CNBD
8.46E-06
<
5.29E-09
<
8.46E-06
CNBD
8.46E-06
<
5.29E-09
<
8.46E-06
CNBD
8.46E-06
<
5.29E-09
<
8.46E-06
CNBD
8.46E-06
<
5.29E-09
<
8.46E06
CNBD
80
16:41
17:11
30
14.587
-------
TABLE J-8
BETHLEHEM STEEL CORPORATION
SPARROWS POINT, MD
KRESS BOX #3
GAS CHARACTERISTICS
Gas Characteristics
Oxygen (%)
Combustible Gases (%)
Static Pressure (ifi. H20)
Time of Measurement
Sin I
BSPAilJ
10/30/91
Run 2
0.5
>5
NMT
12:12
BS-PHCR-1 BS-PHCR-2
1030/91 10/30/91
0.5
>5
NMT
12:32
Sua 3
0.5
>5
NMT
12:S0
NMT
NMT
0.20
12:25
Run 1
BS-PHCR-3
10/30/91
Run 2
1.0
>5
-0.10
14:43
1.3
> 6
-0.30
16:49
1.3
> 5
NMT
16:59
Run 3
1.4
> S
NMT
17:07
Notes:
NMT — No Measurement Taken
All combustible gases were measured at greater thaa 5 percent. The upper limit of die combustible gas meter is 5 percent.
-------
o RECOMMENDATIONS
*¦' ny of 'he test program target compounds were below the detectable limits of the
ar.J; ;ical equipment. In ord2 4-3
r-1 q
-------
Appendix D
Area Monitoring Data Sheets & Analytical Results
Table of Contents
Sect ion Page
1 Summary Tables of Area Monitoring Statistics- D-2
Door Machine vs. K1DC Carrier for Total Particulate
and Benzene Soluble Organics.
2 Table of Total Particulate Sample Database. D-6
3 Table ot Benzene Soluble Organics Database. D-9
4 Table at Ambient Air Sample Database. D-12
5 Report o£ CC/MS Scan tor Organics in Area of Conventional D-14
Pushing Operation from American Medical Laboratories, Inc.
D-l
-------
Section 1
Summary Tables o£ Area Monitoring Statistic-
Door Machine vs. KIDC Carrier for Total Particulate and Benzene
Soluble Otganics.
D-2
-------
AREA MONITORING STATISTICS
OVERALL STATISTICS
TOTAL PARTICULATE CONCENTRATION
NUMBER OF
OBSERVATIONS
AVERAGE
VALUE
STANDARD
DEVIATION
MAXIMUM MINIMUM
VALUE VALUE
DOOR MACHINE
KIDC CARRIER
62
16
10.88
5.75
S. 55
6.73
40.70
22.64
0.52
0.00
BENZENE SOLUBLE PARTICULATE CONCENTRATION
NUMBER OF
OBSERVATIONS
AVERAGE
VALUE
STANDARD
DEVIATION
MAXIMUM MINIMUM
VALUE VALUE
DOOH MACHINE
KIDC CARRIER
61
16
2.14
D.41
2.39
C .24
12.41
0.92
0.04
o.oo
D-3
-------
AREA MONITORING STATISTICS
MOHTHL* STATISTICS
TOTAL PARTICULATE CONCENTRATION
NUMBER OF
OBSERVATIONS
AVERAGE
VALUE
STANDARD
DEVIATION
MAXIMUM
VALUE
MINIMUM
VALUE
DOOR MACHINE
APR91
MAY91
JUN91
JU-91
AUG 91
SEP91
OCT 91
NOV91
4
10
a
:o
:o
a
11
16.85
15.37
9.44
13.37
9.25
3.32
6.53
12.16
13.85
9.77
6.55
7.32
11.34
5.63
4.03
31.90
33.50
24.00
28.50
40.70
21.82
14.50
12.16
3.00
4.75
3.09
6.89
2.16
4.88
0.52
12.16
KIDC CARRIER
OCT91
NOV 91
DEC 91
2
13
1
2.36
5.64
0.08
3.76
7.13
5.53
22.64
0.C8
0.19
O.CO
3.C8
D-4
-------
AREA MONITORING STATISTICS
MOHTHLY STATISTICS
BENZENE SOLUBLE PARTICULATE CONCENTRATION
NUMBER OF AVERAGE STANDARD MAXIMUM MINIMUM
OBSERVATIONS VALUE DEVIATION VALUE VALUE
DOOR MACHINE
APR91
C
3.06
1.60
4.21
0.29
MAY91
10
3.05
1.89
6.CC
0.57
JUK91
a
1.96
1.85
6.34
0.80
JUL9I
10
3.59
4.55
12.41
0.63
AUG91
10
0.83
0.54
1.67
0.04
SEP91
6
0.68
0.56
1.54
0.04
0CT91
9
1.37
1.43
4.05
0.28
NOV91
1
2 .67
•
2.67
2.67
-------
Section 2
Table of Total Particulate Sample Database
D-6
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AKhA MONIIURING PROGRAM TEST RESULTS 11/12 BATTERY 15:22 Tuesday, March 31. 1992
TOTAI PAPTICOIATF O.ONCf NTR A T I ON
KIDC OtMONS:HAfION PROJECT OEIHLCHCM STtCL COKPOHAIION
SPARROWS POINT, MARYLAND
AMl
AML
SAMPl f-
SAMPl F
SAMP. F
AIR
CONCENTRATION
DETECTION
DATC
NUMBER
NUMBER
ID
NUMtJfcR
10CA iUN
WGf. fii
VOL MJ
MG/M3
LIMIT, MG
10/0 4/91
8249363
7180 2411
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8249849
7181 2421
PVC
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DOOR
MATH
9 63
0 80?
1? OO
0 010
10/09/9 1
8249850
7181 2423
PVL
8094
DOOR
MACH
4 64
0. 8bh
5 42
0 010
0/ 15/91
8 253 501
7 ISO 28 91
PVC
8099
DOOR
MACH
7.6b
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9 54
0.010
10/ltt/SI
82b3b02
7 180-2893
PvC
8103
DOOR
MACH
1 ' 76
0 8 11
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0 010
10/23/91
82b3191
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pvl
810b
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MACH
0. 58
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0.010
10/24/91
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MACH
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4 27
0.010
1C)/2b/91
82!>3496
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MACH
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0.752
0. 52
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10/28/91
8253486
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pvc
80-12
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2 1 6
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5.31
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10/29/91
8253506
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6460
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MACH
7.14
0.960
7 44
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11/05/91
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1/20/91
8260729
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PVC
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KRFSS
CAR
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1 i'l 1/31
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11/21/31
8260731
7 183-6063
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92 19
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CAR
3 48
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82607 32
7 183-6064
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1/22/91
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1/21/91
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1 i/24/91
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1/25/91
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0.08
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-------
Section 3
Table ot Benzene Soluble Organics Database.
D-9
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S
0
x co
<30 X
3
X X
X
X
X
Z) X cc
X X
CO
X X
X X
<
z
> t~- r-
P"- > ?>•
r- >
N
h- r-
>
r--
^ ~ "
r- r-
r«-
r-
r- r-
_ 0c © - X r- X) 71 Q
S U C C£ ¦<* T J) 7) O
< n ~i n
3 n O 7> 7i c^!(ncT>o,)
W N N N N S. N. \ S. N. \ N W N 'x N N N yv V Nv \ ^ vv
-{NaDfliuTonTineDaintr, o-trtfiiTvC op- in n « o <3 ^
CCCO-*-N N N\NN sXSNN
G O C O O 3 C O O O O O O O O - - - - cn
D—11
-------
Section 4
Table of Ambient Air Sample Database.
D-12
-------
AREA MONITORING PROGRAM TEST RECUtTS 11/12 BATTERY 15 4 1 lunsday, March 31, 199? 1
A MB IENT AIR DATA BASE
KIDC DEMONSTRATION PROJECT - BETHLEHEM SILLL CURPORAIION
SPARROWS POINT. MARYLAND
AML
AML
SAMPLE
SAMPLE
SAMPLE
AIR
CONCENTRAiI UN
ot 1 tc i IUN
OBS
DATE
NUMBER
NUMRFR
ID NUMRFR
i OCATION
WGT. MG
VOL. M3
MG/M3
LIMIT, MG
1
06/05/91
8232136
7 180-218 1
PVC 7533
BET Cf&SY
0.09
0.930
0.09
O.OIO
2
07/23/91
8237975
7 180-2277
PVC 8326
BET CP&SY
0.01
0.916
001
0.010
3
08/19/91
8242128
7180-2317
PVC 8324
AMRNT AIR
O 00
0 955
o.oo
0.010
4
06/05/91
8232135
7 1 BO 2IfiO
CO 2470
BET CF4SY
0.00
0-902
0 oo
0 020
b
07/23/91
8237974
7160 2276
CO 2307
BET Cf&SY
0.00
0.941
0.00
0.020
6
Oft/ 19/91
8242 124
7180-2316
CO 3€
AMb AIR
o oo
0.907
0.00
0.030
W
-------
Section 5
Report of GC/MS Scan for Organics in Area o£ Conventional
Pushing Operation from American Medical Laboratories, Inc.
D-14
-------
AMERICAN MEDICAL LABORATORIES. INC."
P.O. Box 188 • 11091 Main Street
Fairfax, Virginia 22030-0188
Telephone; (703) 691-9120
PACE
1
INDUSTRIAL HYGIENE DEPARTMENT
xxxxxxxxxx
RECEIVED
RELEASED
REPORTED
WORK ORDER
\1/01/91
02/22/92
02/23/92
50368
7180 BETHLEHEM STEEL CORPORATION
CORPORATE HEALTH fr SAFETY SERV
701 E. THIRD 8T..RM 163A SCO
BETHLEHEM , PA
18016
PROJECT NAME/JOB ID: 400-8691-652
AML NUMBER-
¦VALUE-
-UNITS-
MISCELLANEOUS
Carbotrap 300
10/9/98
Data not provided.
8853481 5 MINUTE FILTER
3280 TDU MASS SPEC SCREEN
TUBE TYPE:
DATE COLLECTED:
TIME COLLECTED:
QUALITATIVE SCREEN:
COMPOUNDS IDENTIFIED
NOTES:
Peak *1 Hexane
Peak 02 Benzene
Peak #3 2,2,3,3-Tetraaethyl Butane
Peak #4 Toluene
ANALYST: Jeffrey Mart In
Probability of Match
91 X
94 %
74 X
83 X
8253482
3280
MISCELLANEOUS
8253483
3280
Carbotrap 300
10/9/91
Data not
10 MINUTE FILTER
TDU MASS SPEC SCREEN
TUBE TYPE:
DATE COLLECTED:
TIME COLLECTED:
QUALITATIVE SCREEN:
COMPOUNDS IDENTIFIED
NOTES:
Peak #1 Benzene
Peak #2 Toluene
Paak #3 Xylan*
Peak #4 Ethyl Benzene
provided.
Probability of Match
95 %
90 5C
95 X
76 %
ANALYST:
15 MINUTE FILTER
TDU MASS SPEC SCREEN
TUBE TYPE;
DATE COLLECTED:
TIME COLLECTED:
QUALITATIVE SCREEN-
COMPOUNDS IDENTIFIED
NOTES:
Jeffrey Martin
MISCELLANEOUS
Carbotrap 300
10/9/91
Data not provided.
Probability of Match
Peak »1
Peak #2
Peak #3
CONTINUED
ON
Methylene Chloride
Hexane
Benzene
NEXT PACE
90 %
78 X
94 X
n 1 *"
IRA D. GODWIN. M.D.
DIRECTOR OF LABORATORIES
-------
AMERICAN MEDICAL LABORATORIES, INC."
P.O. Box 188 • 11091 Main Street
Fairfax, Virginia 22030-0188
Telephone: {7031 691-9120
PACE
INDUSTRIAL HYGIENE DEPARTMENT
xxxxxxxxxx
RECEIVED
RELEASED
REPORTED
UORK ORDER
11/01/91
oe/22/92
02/23/92
50368
7180 BETHLEHEM STEEL CORPORATION
CORPORATE HEALTH & SAFETY SERV
701 E. THIRD ST..RM 163A S60
BETHLEHEM , PA
18016
PROJECT NAME/JOB ID; 400-8691-652
AML NUMBER VALUE UNITS
CONTINUED PROM PRIOR PACE
ANALYST: Jeffrey Martin
NOTATIONS
Analysis Includes a library starch of the 5 largest
peaks, (based on area counts), performed by a
Probability Based Matching (PBM) system, which is a
reverse search of the peak of interest against the
NBS49K library.
Probability is a numerical degree of "natch11 between
the unknown peak of interest and the reference spectra.
Single peaks may have sore than one aatch and are
reported in X reliability of the natch against the
reference spectra. Further infornatIon on percent
reliability say be found in "Interpetation of Mass
Spectra", 3rd edition, F. U. McLafferty, ISBN0-93S702-
04-0.
Conformation of peaks are based on Batching retention
tises and mass spectra* of the peaks of interest and
of reference standards.
FINAL REPORT •••
FRED I. CRUNDER
TECHNICAL DIRECTOR, IND. HYGIENE
FOR INDUSTRIAL HYGIENE RELATED QUESTIONS,
INCLUDING REQUESTS FOR SUPPLIES, CALL
1-800-348-1590
D-16
IRA D. GODWIN. M.O.
DIRECTOR OF LABORATORIES
-------
Appendix E
Alliance Corporation Heport on Quench Tower Emissions & Water Analysis
Table of Contents
Section
1 Alliance Corporation Report on Quench Tower Emissions E-2
2 Quench & Make-up Hater Constituent Analysis Database E-6
3 Quench & Make-up Water TCLP Reports E-9
E-l
-------
Section 1
Alliance Corporation Report on Quench Tower Emissions
E-2
-------
Af4 ALLIANCE
/Wi Technologies Corporation
Date: 25 September 1991
To: C. Vogel, EPA-RTP
From: J. Jeffery, AJliance Technologies Corporation
Subject: Transmittal of Final Inspection Report-Sparrows Point
Attached please find the inspection report containing the emission estimate for Wet Coke
Quench Tower No. 6 at the Bethlehem Steel Facility in Sparrows Point, Maryland.
As no long term total dissolved solids (TDS) data exists at this time, both an equation and a
chart showing anticipated emission rates for various quench water TDS levels have been
presented.
Should you have any questions please call me at (508) 970-5600.
Once again, thank you for the opportunity to be a part of this interesting tasks.
cc: G. Ossman, Bethlehem Steel
R. Fatzinger. Bethlehem Steel
i
-------
ALLIANCE
Tsc~noicc es Corporalion
To:
C. Vogel-EPA/RTP
From: J.
Jeffery-AJliance
Subject: Inspeaion Visit - Bethlehem Steel/Sparrows Point,
Wet Coke Quench Tower No. 6
Background
On Thursday, 29 August 1991, an inspection of the No. 6 Wet Coke Quench Tower was
conducted to determine an estimate of paniculate emissions.
Personnel
Bethlehem Steel
George Ossman - (215) 694-2060
Robert Fatzinger (215) 694-7658
Alliance
John Jeffery - (508) 970-5600
Process Description
The number six (6) or 11 & 12 Battary Quench Tower is a 100 ft. circular brick tower with
an approximate inside diameter of 16.5 ft The tower was constructed in 1953.
Quench water is supplied from a 20,000 gallon holding tank to a series of nozzles made up
from the original set and those installed for use with the Chemico car system. Return water
and make-up water enter via the return water trough. The sump has a breeze filter located at
the spillway wall. The main portion of the sump is clammed on a daily basis. Water is
pumped from this basin to the holding tank.
Approximately 8450 gallons is sprayed on each one-spot car load for about 47 seconds with
the entire quenching process taking 2-3 minutes from the time the car enters the tower until it
exits the tower.
In 1981, a baffle array was installed at the top of the tower. The design is of a "doghouse"
or "tent" nature, with a pitched roof effect and is estimated to be 50-60% effective. The
baffles cover 85-90% of the tower's exit ana are made of reinforced fiberglass. Spacing
3oott Mills South ¦ "cot c? John Stret E_4 /e:!. Massachusetts 01852 ¦ (508) 970-5600
A1 :mpary
-------
/i ALLIANCE
Tecnnclogies Corooration
looks to between 4 and 6 inches and the baffles were constructed at a forty-five degree angle.
This meets equipment standards as set fourth in several states now controlling quench tower
emission (i.e., baffle design, location and TDS water quality).
Emission Estimation
Of the five (5) quench towers that have been tested in the last 15 years in Canada and the
Uoited States, the USX/Lorain Tower best matches the physical and draft characteristics of
Tower No. 6. Both are tall (100 ft) circular brick constructions with exhaust velocities in the
25 to 35 fps range.
A series of tests were conducted in 1976 and 1977 using both "clean" (1000 mg/1 of Total
Dissolved Solids) and "contaminated" (10,000 mg/1 TDS) water. From these tests, a
relationship was discovered between TDS levels and paniculate emissions.
The formula" presented below uses only the results from the USX Lorain Tower tests. It does
not include those from USX/Gary (No. 3 & 5) and DOFASCO (North and No. 1) which do
not match the No. 6 Tower in terms of physical and draft characteristics.
The formula is expressed as E = 131 + 0.000l44y; were
E = Particulate emissions in lbs per ton of coal
Y = TDS (mg/1)
(It should be noted that TDS determinations need to be done at 103-1053 and not at 180°Q.
Without actual TDS data available a range of emission values have been calculated for 500,
800, 1,000, 1,200, and 1,5000 mg/1 TDS levels and are presented as follows:
TDS Emissions
Cmg/H fib/ton coal charged!
500 1.38
800 1.42
1000 1.45
1200 1.48
1500 1.53
2000 1.60
'Final Report, "Coke Quench Tower Paper" U.S. EPA Contract no. 68-01-6316, Task
Assignment No. 43, Table 4, Case D, Pg 19.
jcasCO?6jj
E-5
-------
Section 2
Quench & Make-up Water Constituent Analysis Database
E-6
-------
-------
Bethlehem Steel Corporation
Sparrows Point Plant
coke Oven Division
No. 11 & 12 Batteries
Quench Water Analyses
Pa t e
CNt
As
Pb
Hg
ca
Hard
TSS
TDS
SO 4
CI
OSG
NH3
Phenol
Na
Snlfid*
pH
Temp
ppm
ppm
ppm
ppm
ppm
ppm
ppm
ppm
ppm
ppm
ppm
ppm
ppm
ppr*
pp*
F
03
1D
01
0 14
0 07
0 0?
< 005
4ft
366
2560
249
1121
81
4
O. 12
7 8
IbO
03
26
91
0.24
O.OB
0.C2
< 005
41
396
816
1330
176
463
11
2
0.21
8.5
183
04
09
91
O. 12
0.05
< 20
< 005
101
3 19
420
1200
179
345
5
3
O. 31
188
8 O
175
04
23
91
0.05
0 06
<.20
76
383
575
1644
180
470
33
1
0 18
293
12 0
8 2
180
04
29
91
0.03
0.03
< .20
< . OOb
42
129
393
687
85
99
10
2
0. 15
80
20 0
7 9
162
05
15
91
0.08
O Of
< 20
< 005
BO
387
426
1 101
188
72
<5
1
0.09
167
14 .0
8 0
197
0b
21
91
0.06
0.05
<20
< 005
69
323
381
1 129
18b
82
<5
1
O. 19
194
12.0
7 1
198
05
20
9 1
O 07
O.C6
< . 20
<005
62
280
975
762
1B4
2 12
5
2
0.24
92
10 4
a 1
186
07
25
91
0 12
0.07
< .20
< 005
62
269
560
793
172
189
20
1
0.66
124
1 .6
8 1
198
08
01
9 1
O.OB
O.OB
< . 20
<005
59
280
393
758
337
182
6
1
0.28
130
0.8
8.2
193
08
in
9 1
0 04
0 06
< 005
64
220
698
644
137
139
10
< 1
0.63
106
'2.0
8 . 1
190
08
29
91*
0 12
003
<20
<005
47
212
16B
721
149
152
<5
1
0 25
106
5.6
7 . 7
142
09
10
91*
0 06
0.07
<.20
<005
60
242
303
711
122
186
<5
2
0.39
127
3.9
9.3
146
09
26
9 1 *
012
0 03
<20
< 0O5
72
321
92
1 104
167
196
7
2
O. 29
260
<2 .O
6.2
138
09
26
91
0.07
0.07
<.20
<•005
75
323
1403
1136
172
203
19
3
1 .40
2b2
<4 .0
10
04
9 1*
O. 12
0. 03
< .20
<005
6 1
343
ifcl
1626
172
205
<5
1
O. 36
364
<2 .0
7 9
142
10
OB
9 1 *
O.05
0 03
<20
< .005
60
301
254
1237
144
207
<5
4
O. 32
26 1
<2 O
7 9
140
10
22
91*
<0.02
0 03
< . 20
<005
4b
192
540
613
91
156
<5
3
0 75
1 14
<2.0
7.8
138
10
3 1
91*
O . 27
0 05
.< 20
< 005
70
250
190
904
149
196
-------
Bethlehem Steel Corporation
Sparrows Point Plant
Coke Oven Division
No 1 1 & 12 Batteries
Quench Water Make-up Analyses
Date
CNt
As
Pb
Hg
Ca
Hard
TSS
TDS
S04
C I
O&G
NH3
Phenol
Na
Sul f l«le
PH
T Hmf
ppm
ppm
ppm
ppn
ppm
ppm
ppm
PP™
ppm
ppm
ppm
ppm
ppm
ppm
ppm
J
03 19
91
<0 to
* 02
0.03
<005
24
387
2B
1S71
171
863
104
5
< .05
7 5
59
On 26
9 1
<0 10
< .02
0.02
< 005
25
25G
2B
1010
106
366
5
4
< 05
6 9
60
04 09
91
<0.02
<02
<.20
<005
52
218
12
980
93
339
124
4
<.02
184
6 7
70
04 23
91
<"0.02
< .02
< .20
33
252
6
1 192
97
324
<0
2
<. Ob
207
lb .O
6 - b
66
04 29
91
<0.20
< 02
<.20
< .OCb
31
2O0
6
071
65
8B
16
2
< .05
69
1 6
6 3
70
05 15
91
<0 20
<.02
< . 20
<005
32
194
b
!>83
90
89
19
3
<.05
90
1.2
6 5
85
Ob 2 1
91
0.02
•: .02
< . 20
< .005
34
206
74
763
106
102
4 8
1
0.23
146
1 . 2
7 1
80
05 2B
91
0 02
<02
< . 2()
< CX)b
26
11IH
1 1
324
77
99
<5
2
<05
62
7 6
7 0
86
07 25
91
<0.02
< 02
< . 20
•; 00 b
2b
134
7
454
81
94
11
< 1
< .05
72
0.8
6.2
84
oa 0 1
9 l
<0 02
«• 02
* . 20
< .005
25
110
6
42B
144
97
'5
2
< .05
83
11.2
6 8
87
08 13
9 1
<0 02
< 02
20
< 005
37
1 35
14
434
83
88
<5
< 1
<05
72
<2 0
6 4
86
1)0 23
9 t
O 03
<• 02
<.20
< . 00 b
24
129
B
434
76
92
<5
1
<.05
77
2 . 2
6 8
86
0<1 10
f) 1
<0 02
< 02
< 20
<005
20
121
12
404
67
88
<5
< 1
< 05
66
3.7
6 1
83
09 26
91
<0 0?
< 0?
< 20
< 005
20
1 17
3
366
71
62
<5
1
<.05
. 66
<4 .0
6 4
80
10 34
9 i
<0 02
< .02
< 20
<.005
ill
<4
1720
153
203
<5
< 1
< .05
430
<2 O
G 1
84
10 09
91
<0 02
< 02
<20
<.005
35
255
<4
1121
100
206
<5
2
<.05
265
<2 0
6 6
76
10 22
9 I
0.03
<02
< .20
<.005
34
224
<4
1047
116
206
<5
3
<.05
261
<2.0
6.3
76
10 ?2
9 I *
0.02
< 02
* - 20
«• . COb
34
192
6
980
102
193
c5
2
< 05
182
«:2 .O
6 3
72
10 31
91
0.06
<02
<20
<.005
37
130
b
482
70
1 14
<5
2
<05
85
24.6
6.7
72
10 3 1
9 1 '
0.02
< .02
< . 20
< .005
35
190
I 1
8b 1
96
206
-------
Section 3
Quench & Make-up Water TCLP Reports
E-9
-------
BETHLEHEM STEEL CORPORATION
HOMER RESEARCH LABORATORIES
bethJehem
Analytical Chemistry Group
Bethlehem, PA 18016
Test Report
Client
£rs
-------
73
TABLE OP CONTENTS
Pags(s)
1. TCLP Analysis Request Form 1
2. Metals Analysis 2
3. Volatile Organics Analysis 3
4. Semi volatile Organics Analysis 4
5. Mercury Analysis 5
6. QC Requirements / Holding Times 6
E—11
-------
ess/dmf/Icreq/1 I 02 90
flRllRF 2
TCIP ANALYSIS BEQUfSl FORM- ANAIYlirAl CHCMISIRV GfHJUI> . «t St MICH
tPA PRDIQCOL,
Pro|«rrI Number: Data Submitted: qpifri.....
Requestor: ^fu)alcL
Foe I I Ity:
Data Reported:
Phone No r
;o/m/9/ Iyjtf
Source anri Dnr.crlpt (on of Waste: 3P Pt Cole OKn s &/y Qw>n<& <- ma bop c.b U?s
uate Sampled: y 1 LJafnr
U>
-------
ml 1 !vt64
Analytical Chemistry Group
Homer Research Labs
TCLP METALS ANALVSf 5 REPOflT
<£PA Protocol)
Date Leachate Submitted; 9/27/61 Date Analyzed; 10/7/91
Batch Serial Number; 1029 Anatyst(e)s S. Li
Requester/Facility: Sewa1d/Sparrona Pt Reported bys J. V.
Sample Description; Coke Oven No.11&!2 Batteries Quench Mater
Method: Determination of Heavy Mettle in TCLP Leachates
By Inductively Coupled Plaema Spectrometry
w
i
H
w Ag As 8a Cd C r N1 Pb Se
(mg/l) (mg/1) (mg/1) fmg/1) (ff>0/l) (mg/1) (my/1) (mg/1)
SAMPLE No.
5926 <.05 <.2 <.5 <.02 c.l <.1 <\ 2 <3
5927 <.05 <.2 <.5 <.02 <.1 <.l <.2 <.3
5928 <05 <2 <.5 <.02 <1 <.1 <.2 <.3
(Z^)
-------
VOL 1029
ANALYTICAL chemistry GROUP
HRL
TCLP VOLATILE ORGANICS ANALYSIS REPORT
(EPA PROTOCOL)
1029
01ck Se^aid / Sparrows Point
Coke Oven Hoe 11 & 12 Batteries - Quench
Quench Mater And Quench Mater Makeup
BATCH SERIAL NUMBER:
REQUESTOR/FACILITY:
SAMPLE DESCRIPTION!
RCRA
COMPOUND LIMIT
(COHC. IN PPB) IPPB)
BENZENE
500
CARBON TETRACHLORIDE SOO
CHLOROFORM
CHLOROBENZENE
b.UOU
100,000
1,2-DICHL0R0ETHANE 500
1 , 1-DlCHLOROETHVLENE 700
2 BUTANONE 200.000
VINYL CHIORIDE 200
TETRACHLOROETHYLENE 700
TRICHL0R0E1HYLENE 500
SAMPLE NO.
#5926 LK #5927 LK
<5.00
-------
SV1029
ANALYTICAL CHEMISTRY GROUP
HHL
BATCH SERIAL NUMBER:
REQUESTOR/FACILITY:
SAMPLE INSCRIPTION;
TCLP SEMIVOLATILE ORGANICS ANALYSIS REPORT
(EPA PROTOCOL)
1029
D1ck Sowalcl / Sparrows Point
Coke Oven Nor 11 and 12 Batteries - Quench
Water and Quench Water Makeup
DATE SAMPLES SUBMITTED : 9/27/91
DATE(S) LIQUID-LIQUID EXTRACTIONS 10/1,2
DATE(S) OF ANALYSIS: 10/08/91
DATE REPORTED: 10-14-91
ANAlYST(S)r LM*
COMPOUND
(CONC. IN PPB)
RCRA
LIMIT
(PPB)
SAMPLE NO.
#5926 LK #5927 IK
*5926 LK
2-METHVLPHENO-
(0 CRCSOL)
3&4-METHYL PHENOL
( V.&P C&ESOL )
H HEXACHLOROETHANE
NITR0BEN2ENE
1.4-DICHLGROBENZENE 7,500
200.000
2nn,000
3.CG0
2.00U
HEXACHLOROBUIADIENE 500
2,4,6 TRICHLOROPHENOL 2.000
2 , <1 , 5-Tfi ICHi-OROPHENOL 400,000
2.4-DINI rROTOLUEN'C 130
130
HEXAO ILOROBENZENE
PENT ACHLOROPHENOl
PYRIOINE
100,000
5,000
<10.00
45.9
58 . 9
^10.DO
<10.00
<10.00
<10.00
<10.00
<50.00
<10.00
<10.00
<10.00
<10.00
<10 .00
<10.00
<10.00
<10.00
<*0.00
-------
Jy1/tc1phg
10/07/91
163v102
Analytical Chemistry Group
Homer Research Labs
TCLP MERCURY ANALYSIS REPORT
(EPA Pro toco 1)
Date Leachate Submitted: 9/27/91 Date Analyzed: 10/4/91
Batch Serial Numberi 1029 Analyst: S. L1
Requester/Plant; Sewa1d/Sparrows Pt Reported byi J. V. Hi
Samp]# Descriptions Coke Oven No 11& 12 Batteries Quench Water
MethoC: Determination of Mercury in TCLP Leachates by Cold-Vapor Atomic Absorption Spectroacopy
Ho
Samp)e No. (ug/t)
59261k < 5
ra
^ 59271k < 5
<7\
59281k < 5
(5)
-------
EPA 1029
QC REQUIREMENTS / HOLDING TIMES
BATO' SERIAL NO.:
SAMPLE NOS.:
1029
5926 - 0926 Lk
SAMPLE DESCRIPTION: Coke Owen No». M & 12 Ouanc* Water ana Quench Watsr Makeup
SAMPLING DATE; 9/26/91
ANALYSES REQUESTED; template TCL Metals, Semi vo 1 at U «&, Volatlles
ORIGINAL flLLS STORED IN C-182 UNDER FIlE NO: 1029
SAMPLES ANALYZED IN ACCORDANCE WITH ALL EPA PROTOCOLS AS OUTLINED IN SW-Q46 AND INTERPRETED BV THE ANALYTICAL CHEMISTRY GROUP.
ALL EPA MANDATED QA/QC REQUIREMENTS WERE MET WITH THF EXCFPTION OF THOSE LISTED BELOW. KEY DATES ARE LISTED BELOW TO VERIFY HOLDING
TIMES. ALL ADDITIONAL QC DATA IS AVAIIABIF UPON REQUEST.
DATE OF SAMPLE RECEIPT
DA IL OF 1CLP EXIHAC I I ON
DATE OF ZHE EXTRACTION
METALS
9-27-91
NA
SEMIVOLATILES
9-27-91
NA
VOLAULE5
9-27-91
NA
H0
9-27-91
NA
DATE OF LICUID/LIOUI0
EXTRACTION
NA
10/1.2
DATE 0C ANALYSIS
10-07-91
SL
10-08-91
9-30-91
10-04-91
COMMENTS/EXCEPTIONS:
(L)
-------
BETHLEHEM STEEL CORPORATION
HOMER RESEARCH LABORATORIES
BETNiEHEM
Analytical Chemistry Group
Bethlehem, PA 18016
Test Report
Client
Address
Serial No. 10~2 3
Material _OcHfr •*" Ke -U p l^Cfkr"
i|) *¦ *\ 'X fca'Uerits
Receipt Date
Report Date -3M15L
Reported By
Title
Page 1 Of j&.
S-18
-------
73
TABLE OP CONTENTS
Page(s)
1. TCLP Analysis Request Fora 1
2. Metals Analysis 2
3. Volatile Organics Analysis 3
i. 5emivolatile Organics Analysis 4
5. Mercury Analysis 5
6. QC Requirements / Holding Times 6
E-19
-------
ess/dwf/tct eq/ 1I-Q2-90
FIGtIRL 2.
1CLP ANALYSIS WE QUI S 1 rOQM - - ANM.V I I CM CMEMIS1R* GROUP
EPA PROI
Oat a SufcwnIt ted: ...//<5- &i{Ws
hWi-uf u-6-t?-
j^Xj Od
(I)
-------
mI 11v164
Analytical Chamlatry Croup
Homer Ratearch Labs
tCLP M£TAUS ANAUVSiS REPOR1
(EPA Protocol)
Date Leachate Submitted: 9/11/91
Batch Ser ial Number i 1023
Requester/Facility; 0 Sewa1d/Sp»rro»s Pt
Sample Description! Cokt* Oven No. 11112 Batteries Quench Mater
Data Analyzed: 9/19/91
Analyst(s ) : S. Li
Reported Oy: J. V.
Method; Oeterrrtnat 1on of Heavy Metetle In TCLP Leachatea
By I nductlvely Coupled Plasma Spectrometry
m
i
ro
SAMPLE No.
5887
5386
5889
*0
(mg/1)
<.05
<.05
< .05
AS
(mg/I)
<.2
<2
<.2
Bl
(mg/Ii
<-5
< . 5
<.5
Cd
(mfl/1)
<.02
<.02
<.02
Cr
(mg/J)
<. I
<. I
< . I
Nf
(mg/1)
<. 1
<. 1
<. 1
Pto
(mg/1)
<.2
<.2
<.2
Se
(mg/1)
<•3
<.3
<.3
(Z)
-------
vm 1023
ANALYTICAL CHEMISTRY GROUP
HRL
T CLP VOI A T I i fc ORGANICS ANALYSIS REPORT
(EPA PROTOCOL)
BAICH SERIAL NUMBER: 1023
REQUfcSIOR/fAUILITY. DiCk bewaId / Sparrows Point
SAMPlE DESCRIPTION Coku Oviin Nub II & 12 Batteries - Quench
Quench Water And Qunnr.h Water Makeup
RCRA
COMPOUND lIMIf
(COHC IN PPR) (PPBJ
RFNZf-NE bOO
CAKflUN II IRAClIt 0R1DE bOO
SAMPLE NO.
.-/'jBB; LK *5868 lk
CtlLOROF OHM
b . ooo
CHLOROtUNZfcNfc 100,000
I,2 ~PfCHLOROETHANf 500
l.l UICHLUPOCTIIYI CNC 700
2-8Ur ANDNt 200.000
VINYL CHLORIDE 200
I Z TRACl il OROf THY1 ENE *00
IR ICHLOROE Tl IYI ENE 500
-------
SV 1023
ANALYTICAL CHEMISTRY GROUP
NRL
TCI P SEMIVOLAHLE ORGANICS ANALYSIS REPORT
(fcPA PROTOCOL)
BATCH SERIAL NUMBER: 1023
REQUI- STOR/F AC IL 1TY : Dick Sowald / Sparrows Point
SAMPLE DESCRIPTION: Coke Oven Nos It arid 12 Batteries - Quencn
Water and Quench Wuter Makeup
H
COMPOUND
(CONC. IN PPB)
RCRA
i iwit
(PPB)
1.4 DlCHLOROetHZENE 7.SCO
2-MCTHYlPHtNOt
(Q-CRESOi.)
38-4 METHYLPHENOL
(M&PCRESOL)
200,000
500.000
3.000
2.000
hexachlurqetiiane
nitrobenzene
HEXACIU OROBUT AD IENfc bOO
2.A. 6-TRICNlOROPHENOI 2.OOO
2.4.5 TfclCMLOROPHENOl 400.000
2 . -1-UINITROTQUJENE 130
Hf- X ACHLQRUULNZLNL 1 JO
I'tNI ACHl OROPHFNOI 100 . 000
PYRlDiNf- 5. OCX)
SAMPLE NO.
iC5BB7 LK #5BB8 LK
< 10 00
< 10 00
<¦50 . OO
< IO oo
<10.OO
<10.00
<10.00
<10.oo
¦mo.oo
<10.00
<10.oo
<10.00
-------
JyI/tcIphQ
09/23/91
I63v102
Analytical Chemistry Group
Homer Research Labs
TCLP MERCURV ANALYSIS REPORT
(EPA Protocol )
Date ieachate Submitted: 9/11/91 Data Analyzed] 9/18/81
Bateft Serial Number: 1023 Analyst: S. LI
Ruquua tor/Plant t 0 SoNStd/SpHrroMb Pt Reported by: J. V. Liu
Sample Description; Cone Oven No 11112 Batteries Quench Water
Method: Determination of Mercury In TCLP leachatea by Cold-Vapor Atomic Absorption Spectroscopy
Ho
Samp 1e No. (yg/I)
58B71H < 5
PJ
^ 5888 1k < S
58981k < 5
(S)
-------
EPAREP997
00/24/91
OC REQUIREMENTS / HOLDING TIMES
BATCH SERIAL NO.; 1023
SAMPLE HQS..- 5887 - 5869 Lk
SAMPLE DESCRIPTION: Cokt Ov®n Nos. 1 1 & 12 Quancft w*t«r »r»d Quanch Watar Makaup
SAMPLING DATE: 9/10/91
ANALYSES REQUESTED; Camp lata TCLP; Sam1vol at1 Iaa. Volatliaa
ORIGINAL FILES STORED IN C-182 UNDER FILE NO: 1E123
SAMPLES ANALYZED IN ACCORDANCE WITH ALL EPA PROTOCOLS AS OUTLINED IN SW-846 AND INTERPRETiD BY THE ANALYTICAL CHEMISTRY GROUP.
ALL EPA MANDATED QA/QC REQUIREMENTS WERE MET WITH THE EXCEPTION OF THOSE LISTED BELOW. KEY DATES ARE LISTED BELOW TO VERIFY HOLDING
TIMES. ALL ADDITIONAL QC DATA IS AVAILABLE UPON REQUEST.
DATE OF SAMPLE RECEIPT
METALS
9-11-91
SEMIVOLATILES
9-11-91
volatiles
9-1 1-91
Hfl
0-1i-91
DATE Oh TLLP LXiKACIION
m
i
^ DATE OF ZHE EXTRACTION
NA
NA
NA
DATE OF LIQUID/LIQUID
EX!FACTION
9-11,12
HA
DATE OF ANALYSIS
ANALYST
SL
9-16-91
9-1891
9-19-91
SL
COMMENTS/EXCEPTIONS;
(U)
-------
BETHLEHEM STEEL CORPORATION
HOMER RESEARCH LABORATORIES
Analytical Chemistry Group
Bethlehem, PA 18016
Test Report
Client
WL
Address nhs.'
Serial No S3.Z
11 ~ i >-
Material
Q"CL n uJurtc
Receipt Date jInISL-li^iht—
Report Date —Sllklll
Reported By
Title £&SQlLLJke.k&ZL
Page 1 Of —3
E-26
-------
73
TABLE Qg CONTENTS
Page(s)
1. TCLP Analysis Request Form 1
2. Metals Analysis 2
3. volatile Organics Analysis 3
4. Semi volatile Organics Analysis 4
5. Mercury Analysis 5
6. QC Requirements / Holding Tines 6
E-27
-------
ra
i
«ss/dmf/tcreq/ 11-02-90
FIGURE 2
-tsp-^)OOg
TCLP ANALYSIS REQUEST FORM ANAIY1ICM C1IEH151RY CROUP. RESEARCH
EPA PRHIOCOL
Project Number:
Requestor;
Source and Description of Woslo:
DoIh Sampled;
PRHIOCOL
If/t/V . .
Fac11 Ity: Sf><\f/o\»3 Pi.
Date Submitted:
Date Reported:
Phone No. ;
r//<>/?/
¦ 7j/o/11
CoU^O\/en Mis
(^ugvi<^ tAJcJ^* G v;
Pb NI S« Hq reeta
hfiJtach I orobenzene hexachlorobu t ad I en* hftxacht or o thane
pyridine 1.4-dlchlorobenzene o-cresal
_P"Cr**°l pentachlorophenol 2.4,S--tr Ichlorophanol
( a 11 aerel-volat I lejp
carbon tetrachloride chlorobenzena chloroform
1. 1 -dlchloroethane I, I dIchloroathy lene raethyl ethyl ketone
trIchlorethylene vinyl chloride ^bH volat Heap
Unknown Materials:
Lab. No. UescrIptton(15 characters max.)
•ZI&f.Lt- QtrPT (aKcOttn* (Sotnik \/ja7a£ mfiOEiP-I
5735L)L SP Pr (0\_f V{<<\ Queoth uW((L-
C>P PC b,tc Ovtn tymr h f(\QU--Of J-
-------
ml 11vl64
Analytical Chemistry Group
Homer Research Labs
TCLP METALS ANALYSIS REPORT
(EPA Protocol>
Date Leachate Submitted: 7/11/91 Date Analyzed: 8/12/01
BetCh Serial Number: 997 Analyst(s); S. H
Riquiit«r/F»c
-------
VOL997
BATCH SERIAL NUMBER:
REOUESTOR/FACILITY:
SAMPLE DESCRIPTION;
ANALYTICAL CHFMISTRr' GROUP
HRL
TCLP VOLATILE ORGANICS ANALYSIS REPORT
(EPA PROTOCOL)
997
George Ossraan / Sparrows Point
Coke Oven Nos 11 & 12 Batteries - Quench
Quench Water And Qunnnh Water Makeup
COMPOUND
(CONC. IN PPBI
CARBON T E1RACHLORIPE
CHIQRGFURM
CHIQROBENZENE
1 .2-niCHt OROETHANE
1 , 1 -DICHLOROF f HYL fcNfc
2-BUT ANONE
VINYL CHLUR10C
TETRACHLOROETHYLENE
TRICHLOROETHYLENE
RCRA
LIMIT
(PPB)
500
500
6.000
100.000
500
700
200.000
200
700
500
SAMPLE NO.
#5724 LK #5725 LK
<5.00 <5.00
<5 OO <5.00
19.2 <5.00
<0.00 <5.OO
•*5. OO
<*5.00
<100.O
*5726 LK
<5 00
<5.00
23.9
<5.00
< 5 00
<5.00
<100.0
<5 OO
<5.00
<5.00
-------
SV937
ANAL V I I CAL CHFMISrRY GROUP
HRL
TCLP $EM1VOLATILE ORGANICS ANALYSIS REPORT
{CPA PROTOCOL)
bAlCH SERIAL NUMBER. 99?
REQUESTOR/FACILITY: George Ossman / Sparrows Point
SAMPLE DESCRIPTION: Coke Oven Nos 11 and 12 Batteries - Ouench
water and Quench Water Makeup
M
i
COMPOUND
ICONC. IN PPB)
RCRA
LIMIT
(PPB |
1. 4 -DICHl OROBFNZENE 7 , 500
300.000
2CX), OCX>
3.000
2,000
HFXAOHl ORQBUTADICNE 500
2.4,6-1RICHLORDPHFNOi 2 .000
2.4 .5-TRICHLOROrHENOi. 400.000
2,4 0 INIIRD [ QLUt Nfc 1'JO
2-Mt IHVLPHtNlll
IO-CRES0L)
3&4-ME T HYL PHENOL
(M&P-CRE50L|
hexachloroethane
NI TRflBFNZFNE
HE X ACHLOROKfrNZFNfr
UO
PENTACHLQROPHENOL
100.000
5,000
SAMPlE NO.
#5724 LK #5725 LK
<• 10 oo
<¦10.00
<10 00
< 10 oo
OO 00
<,10 00
<10-CO
<10.00
24 8
b(> 2
< 10.00
oo oo
< 10 OO
< 1000
< 10. OO
< 10.00
oo oo
<50 00
<10.00
M)
DATE SAMPLES SUBMIT TED ; 7/11/01
0ATE(SJ LIQUID LIQUID EXTRACTION; 7/15.16,
DATC< S ) OF ANALYSIS: 8/05/91
DATE RtFURILO. 8/1G/91
ANALYST(S J: I MP
#5726 LK
<10.00
<10.00
<10.00
< 10 00
<10 OO
< 10 00
<10.00
< 1000
< to.oo
< i o co
<50.00
<10.00
-------
Analytical Chemistry Group
Homer Research Labs
TCtP MERCUftV ANALYSIS REPORT
i EPA Protocol)
Date Laachata Submitted: 7/11/91 Data Analyzed: 7/30/91
Batch Serial Humbert 997 Analyst; S. L1
Requester/Pi art: Oaairtan/Sparroxa Pt Reported by; J. v. Liu
Sample Description! Coke Oven No 11&12 Batteries Quench Water
Method.* Determination of Mercury 1n TCLP lenchates by Cold-Vapor Atomic Absorption Spectroscopy
Ha
Samp1 a No. (u©/1}
57 241N < 5
n
I 57251k < 5
u»
to
57*etk < 5
JyI/tc1phg
OB/14/91
I63v10?
15)
-------
EPAREP997
08/16/91
0C REQUIREMENTS / HOLDING TIMES
BATCH SERIAL NO .
SAMPLE NOS.'
SAMPLE DESCRIPTION
SAMPLING DATE:
997
5724 - 5726 Lk
Coke Oven Nos. 11 & 12 Quench water and Quench Water Makeup
7/IG/91, 0/13/91
ANALYSES REQUESTED; Complete TCLP: Metals. SemIvoIa11»es. Volatlles
ORIGINAL FILES STORED IN C-102 UNOER FILE MO: 997 AND NOTEBOOK 129
SAMPLES ANALYZED IN ACCORDANCE WITH ALL EPA PROTOCOLS AS OUTLINED IN Stf-848 AND INTERPRETED BY THE ANALYTICAL CHEMISTRY GROUP.
ALL EPA MANDATED OA/OC REQUIREMENTS WERE MET WITH THE EXCEPTION OF THOSE LISTED BELOW KEY DATES ARE LISTEO BELOW TO VFRIFY HOLDING
TIMES- ALL ADDITIONAL QC DATA IS AVAILABLE UPON REQUEST.
DATE Of SAMPLE RECEIPT
DATE OF TCLP EXTRACTION
DATF OF 2HE EXTRACTION
DATE OF LIQUID/LIQUID
EXTRACTION
METALS
7-11-91
NA
NA
NA
SEM1V0LATILES
7-11-91
NA
NA
7-15, 16. 17
WOLATILCS
8-14-91
NA
NA
Hg
7-11-91
NA
NA
NA
DATE OF ANALYSIS
ANALYST
8- 12-91
8 05-91
LMP
a- 15-91
SL
COWMEN I
s/except ions gpsutotfbhj m p//s/9J stLujl to jsl Jokrftlp rifawc* Ortitys*-
(i*")
-------
APPENDIX F
Kress Bulletin* and Photographs of the KIDC Operation
•Reproduced with permission of Kress Corporation, P. O. Box 368, Brimfield, IL 61517.
F-1
-------
KIDC system in testing at
Bethlehem Steel
Kress Corporation's innovative kidc (Kress
Indirect Dry Cooling) coke handling system is now in testing
at one of America's leading steel plants, the Bethlehem Steel
Corp. location at Sparrows Point, MD. The KIDC system
controls pushing and quenching emissions, and is expected
to improve coke quality and yield. The system plans
include door extracting and cleaning as well as jamb
cleaning. This then eliminates the need for traditional coke
side operations, including conventional door machines, coke
guides, quench cars, quench towers, breeze ponds
and wharfs. Also replaced will be hoods, sheds and
conventional dry quench systems, plus conventional door
and jamb cleaning systems. (continued/
f
4 I *11 )
-------
Other K1DC Advantages
In addition 10 ail the advantages gained
through elimination of pushing emissions
and conventional coke side operations, it is
anticipated that the KIDC will improve coke
yield for a variety of reasons: the coke cake
maintains its in-oven form as it enters the
box, so it stays intact as it cools. The coke
is cooled slowly, does not burn, and in not
shocked by the common water quenching.
Laboratory tests have shown that KIDC-
cooling improves coke quality.
KIDC components and operation
The KIDC system includes a vehicle, a series
of boxes la single box will serve approa
matcly six ovens), a cooling rack with space
for each box. and a receiving station.
During the push, the box is sealed at the
jamb, and when the push is completed, a
guillotine door closes and the box is
automatically sealed. Water flows over the
box at all times except when at the receiver
station. Oven door leakage is expected to be
reduced, since the door and jamb will be
cleaned with the latest technology during
each push. Door replacement is
accomplished with an alignment system
designed for accuracy and reliability.
Following the push, the KIDC vehicle
transports the box to a cooling rack. An
adjacent cooled box is then loaded onto the
carrier and transferred to the receiving
station, where the cooled coke is deposited
into a hopper that is designed for
environmental soundness, and onto the
conveyor system. The coke is then
transported to the blast furnace. KIDC cycle
time is designed to be approximately 8 :/2
minutes and the entire cycle is planned with
no operator involvement required,
eliminating human error.
For more information
Find out how the KIDC system can work for
your operation. For more Information
and details on current operations, contact
us today.
,-CONTi Nk.l COOP
ACTUATOR
OV3. 300R S JAMS
Cleaner, handier
-TltTCVLNOE*
T „T ffRAMg
1/
jC] *¦¦*-
V
!i
Uj
rjin
Li 1
J M
SWING FR«if
1 CONTAINER EXCHANGE
ft Ml
CAxmm
Tf=AV=U%G TO
COOLING RAC-;
CAH- ER HANDLING
Ov£'» 0Q3* AND
C.EJVNG.AMB
CAF3I6R
AT OVEN
ftfGEIV HC>
CCKE
CARPIER PA.lt
nffi
' " 1 COCJNGRACK
FOP My iT PLi
CONIAINE^b
BATTER"*
flFC? VF=
AUXILIARY StAl.C'^
DUMPING l/\
STATION *
wff
w
CaFUVFA «iyiTt«
IIL1EDBOX
DUMP MG
CO*£
K
COFc-
K^ESS CORPOPATICM
loss
Ai H;£M$ Hese'ved
KRESS CORPORATION
P.O. Bo* 3S8
RimliOd. iHmoiS 615"? US£
Pnare: (309) M6-333i
TWX: 91C-£5'-42S0 FAX: !239« 446-9S2b
Av.siue Oi! I,! i anc.P. 2
1" 63 Brussels Belgium
PW); 1021C74-5213 FAX; , S74-5237
K«£5a J'iC H .j-i' T' EC^rr'ir.o! K-c'-s J*—3 ,n
-------
F-4
-------
F-5
-------
KiCC carrier in pt>s i r i on > 3c:e|.i a poii
r-6
-------
F-7
-------
Bac\ of a KIDC box after accepting a pusn witJJ fia
F-8
-------
KIDC box in travel ir.odt? to ccoiing rack after accept i rsy a liusti
with fiaie stacK ignited
F-9
-------
KIDC cooling station
F-10
-------
firepji i rig tot
F-ll
-------
F-12
-------
KIDC carrier discharging c..h# witD the roce:v=, station
witr, auxiliary receiver stat ...o sr.cwu in -.lie :oi t • i ;.-ur.d
F-13
------- |