United States Region 6 EPA 906/9-79-007
Environmental Protection 1201 Elm Street March 1979
Agency Dallas, Texas 75270
<&EPA Evaluation and Processing
of Houston Area Emission
Inventory Data
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• United States Region 6 EPA 906/9-79-007
Environmental Protection 1201 Elm Street March 1979
Agency Dallas, Texas 75270
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EPA # 906/9-79-007
EVALUATION AND PROCESSING
OF HOUSTON AREA
EMISSIONS INVENTORY DATA
March 31, 1979
Prepared by
D. B. Cabe
K. K. DeBower
M. A. Magee
Radian Corporation
Austin, Texas 78766
for the
U. S. Environmental Protection Agency
1201 Elm Street, Suite 2800
Dallas, Texas 75270
Contract # 68-02-2538
Task # 3
Randall Brown, Project Officer
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DISCLAIMER
"This report has been reviewed by Randall Brown, EPA Region 6, and
approved for publication. Approval does not signify that the contents
necessarily reflect the views and policies of the Environmental
Protection Agency, nor does mention of trade names or commercial products
constitute endorsement or recommendation for use."
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PREFACE
The value of air pollution emission inventories can be increased if the
data from these inventories can be easily accessed to produce various
data summaries and reports and to provide for inputs to predictive models
and other data bases. This program was funded by the Environmental
Protection Agency, Region 6, to increase the usefulness of point source
emission inventory data bases gathered by the Texas Air Control Board.
This report describes the results of this program.
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ABSTRACT
This project was initiated with the overall objective of providing the
Texas Air Control Board (TACB) with a computerized emissions inventory
data base for point sources in the Houston area. This data base, when
accessed by programs developed by the TACB, can be used to generate
National Emissions Data System (NEDS) data reports, to provide other
emissions inventory reports useful to the TACB, and to provide point
source emissions and stack inputs for dispersion modeling studies.
Point source questionnaires were evaluated for completeness and correct-
ness and data were coded onto specially designed and organized screens
or forms. Data from those screens were then keypunched, and punched cards
were processed by computer programs designed to edit and reformat the data.
Finally, computer tapes were generated from this keypunched data and
delivered to the TACB. In summary, emissions inventory data for over 2800
individual point sources were evaluated, coded, and processed.
This report is submitted in fulfillment of Contract No. 68-02-2538 by
Radian Corporation, under the sponsorship of the U.S. Environmental
Protection Agency. It summarizes the results of this data evaluation and
processing activity. The report covers the period from August 1, 1978, to
March 30, 1979.
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ACKNOWLEDGEMENT
The cooperation of Mr. John Anderson and the staff of the Emissions
Inventory Section of the Texas Air Control Board is gratefully acknow-
ledged. In addition, we are grateful for the advice and assistance of
Mr. Tom Shirley and Mr. Bill Stadig of Radian Corporation in the engineer-
ing evaluation of the emissions inventory questionnaires.
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CONTENTS
Page
Preface iii
Abstract iv
Acknowledgement v
Introduction 1
Summary of Results 3
Engineering Evaluation 7
Data Coding 9
Computerization Data Processing 11
Appendices
A. Instructions for Evaluating Questionnaires 13
B. Sample Texas Air Control Board
Emissions Inventory Questionnaire 17
C. Emissions Inventory Questionnaires
Containing Data Not Coded 37
D. Instructions for Coding 1975 Emissions Inventory Data .... 39
E. Keypunching Instructions for Emissions
Inventory Coding Forms 79
F. Programmer's Guide to the Edit and Reformat Programs 85
G. SCC List 97
H. Pollutant Code List 151
I. Questionnaire Activity Summary 161
vi
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SECTION 1
INTRODUCTION
This report presents the results of a study to provide engineering
evaluation and data processing for 2000 or more emission points from the
1975 Texas Emissions Inventory Questionnaires for the upper Texas Gulf Coast
area. During an eight month effort performed by Radian Corporation for the
Texas Air Control Board (TACB), approximately 2800 individual emission sources
were evaluated and pertinent source information was coded on special coding
screens designed for use in keypunching coded data. These data were then
processed by specially designed editing and reforming computer programs,
and magnetic tapes containing processed emissions inventory data were
submitted to the TACB.
This work was performed in response to the need, identified by EPA
Region 6 and the TACB, for the development of a computerized point source
emissions inventory data base. This data base, when accessed by programs
developed by the TACB can be used to generate National Emission Data System
(NEDS) data reports for the Environmental Protection Agency (EPA), to provide
other emissions inventory reports useful to the TACB, and to provide point
source emissions and stack inputs for dispersion modeling studies.
One of the initial steps in establishing this computerized emissions
inventory data base was the evaluation and coding of the extensive Texas
point source emissions inventory. The inventory data, in the form of hard-
copy questionnaires prepared by individual companies, required engineering
evaluation, summarization, and coding before entry into the TACB's computer-
ized emissions inventory data base. Because of manpower limitations, the TACB
elected to use contract labor to accomplish part of this task.
Radian Corporation was selected to perform the data evaluation and coding
of major point sources in Galveston, Brazoria, and Harris Counties. At the
outset of the project, it was decided that approximately 2000 individual
emissions points would be evaluated and coded. This number represents the
TACB's initial estimate of the number of major sources of criteria pollutants
in the three-county area.
The remainder of this report summarizes the work performed during each
of the individual tasks involved in the evaluation, coding, and computer
processing of the emissions inventory data. Section 2.0 presents the results
of the study and Sections 3.0, 4.0, and 5.0 summarize the activities asso-.
ciated with the engineering evaluation, coding, and computer processing
activities. Appendices A through F contain specific reports delivered to
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the Texas Air Control Board as an output of this study. Appendices G and H
contain complete lists of the two most important codes used in the study,
SCC (Source Classification Codes) and Pollutant Codes. Appendix I summarizes
the evaluation and coding activities performed for each questionnaire.
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SECTION 2
SUMMARY OF RESULTS
The following tasks were accomplished during this project:
2831 individual point sources of criteria pollutants were evaluated
and coded. Information for these 2831 point sources was combined in
such a way that coded data for 1836 "grouped" point sources was sub-
mitted to the TACB. This represents almost all point sources in the
1975 TACB emissions inventory for Harris, Brazoria and Galveston
Counties with particulate emissions >^ 25 tons/year and emissions of
any other criteria pollutant >_ 200 tons/year. The only point sources
not evaluated and coded were storage tanks and those point sources
included in confidential sections of the questionnaires.
A set of 15 forms or screens was developed for organizing and codify-
ing raw questionnaire data so that they could be put into a format
suitable for entry into the TACB computerized data file.
Approximately 8000 screens were encoded and keypunched.
Computer programs were prepared to edit and reformat the keypunched
data. The edit program read the keypunched data to make simple tests
(e.g., range checks, absence of some mandatory information) on the
data, and to produce printed output identifying erroneous data. The
reformat program was used to read the edited data file and to produce
card-image data files in the format of the TACB emissions data base.
Programmers' manuals and magnetic tapes containing the program codes
were prepared and presented to the TACB.
Eleven magnetic data tapes produced from edited and reformatted data
were presented to the TACB. These tapes contain the information
coded on the 15 screens for each of the approximately 2800 emission
points evaluated.
Data on tapes were and continue to be evaluated by the TACB. Errors
discovered are documented in error reports presented to Radian
Corporation. These errors are corrected and new data tapes produced
for the TACB.
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At the time of preparation of this final report, the TACB had not
completed its evaluation of all the magnetic data tapes supplied by
Radian. It is anticipated that this review process will continue for
approximately 1-2 months beyond the date of this report. Subsequent
data correction, keypunching and regeneration of new data tapes by
Radian will take an additional 1-2 weeks beyond the date of receipt
of error reports from the TACB.
The sequence of activities performed in the evaluation, coding, and
computer processing of emissions inventory data during this project is
summarized in Figure 1.
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EMISSIONS INVENTORY QUESTIONNAIRES
ENGINEERING
EVALUATION
OISK-TO-TAPE
UTILITY PROGRAM
MAGNETIC DATA
TAPE FOR TACB
STORAGE ON
TACB DISK FILE
CODING FORMS
Figure 1. Sequence of Data Evaluation, Coding,
and Processing Activities
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SECTION 3
ENGINEERING EVALUATION
The first step in producing the computerized data file was to perform an
engineering evaluation of the data entered on the emissions inventory
questionnaires prepared by the individual companies. The purpose of this
evaluation was to identify missing or inaccurate data and to obtain sufficient
data to characterize emissions and stack parameters for the sources encoded on
the coding forms or screens.
During the early stages of the program, Radian personnel met with TACB
engineers to discuss procedures to be used in evaluating and coding question-
naire information. Following these meetings, Radian personnel obtained
company questionnaires from the TACB and performed the questionnaire
evaluations in the Radian offices. The staff evaluating these questionnaires
were supervised by a Radian environmental engineer and advised by senior
chemical engineers.
The specific procedures and guidelines used by Radian personnel in
evaluating the questionnaires are presented in detail in Appendix A, which
is a working document. Appendix B is a sample of Texas emissions inventory
questionnaires. The evaluation procedures described in Appendix A are sum-
marized below.
• Confidential information contained in the questionnaires was not eval-
uated, but instances in which such data were not evaluated were docu-
mented.
• Only sources from Harris, Galveston, and Brazoria Counties (the
Houston area) were evaluated.
• Only those sources with particulate emissions greater than 25 tons/
year or emissions of any other criteria pollutant (SOa, NO , CO,
hydrocarbons) greater than 200 tons/year were evaluated.
• Within the selected source files, only those specific emission points
with emissions greater than 10 tons/year or 4 pounds/hour of a
criteria pollutant were considered.
• Source emissions not already evaluated by the TACB were verified by
material balance calculations, the use of emission factors, contacting
companies, and other methods.
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Questionnaires were closely examined by the Radian personnel, so that
they could obtain a familiarity with the basic functions of each
plant as well as how various processes related. Checks were made for
internal inconsistencies within the questionnaire, and such inconsis-
tencies were resolved.
All assumptions involved in the evaluation, all telephone contacts
with companies, and all cases in which confidential data within a
file were not evaluated and coded by Radian were documented.
(Appendix C contains a list of all questionnaires containing confiden-
tial data not evaluated and coded by Radian Corporation).
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SECTION 4
DATA CODING
Once evaluation and correction of questionnaire data were completed for
each 1975 emissions inventory account, required information was coded onto
specially-designed screens or forms using the format developed by the TACB.
A user's manual of coding instructions is included as Appendix D to this
report. Appendix I summarizes the coding activities performed for each
questionnaire.
All types of emissions sources reported in the 1975 TACB Emissions
Inventory questionnaires were coded with the exception of storage tanks.
Types of sources coded include processes, abatement devices, stacks, flares,
loading, and fugitive polluted sources. Eleven categories or "sequence
types" were developed by the TACB for coding the above referenced sources.
Information required for each sequence type was coded onto "screens," or
hard-copy coding sheets. A total of 15 screens was used. Various combina-
tions of these screens comprise the sequence types.
The sequence types representing processes, abatement devices, stacks,
and process fugitives are related to each other in a linear flow pattern by
means of the network, which is a sequence type unto itself. In the coding of
data, links of pollutant flow were connected to one another, starting with the
process generating emissions, passing through abatement devices which remove
pollutants, and ending with final emission points to the atmosphere in the
form of stacks or process fugitives.
Certain throughput cut-offs were supplied to Radian by the TACB to sup-
plement the 10 tons per year or 4 pounds per hour emission cut-offs. One
feature of the coding system involved grouping, whereby small sources whose
throughputs or emissions were under the cut-off could be combined so that the
grouped sources met or exceeded the cut-off limits.
Another feature of the coding system allowed for an accounting of changes
in process, abatement, and stack configurations over time. The TACB regula-
tion V required that certain sources of volatile organic hydrocarbons meet
emission regulations by May 31, 1975. For many sources this regulation
required the installation of abatement equipment in mid-1975. In this study,
a stack which emitted at uncontrolled rates until mid-year abatement went into
effect was coded separately for uncontrolled and controlled emission rates.
The respective time periods for each mode of operation were also recorded.
According to the work plan for this project, confidential information
withheld from questionnaires was to be evaluated and coded by the TACB, not
by Radian. (Appendix C lists these accounts or questionnaires) The
confidential accounts fell into two categories:
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• Accounts with sufficient information to code processes and associated
emission points—only production figures, operating rates, or.feed
materials were missing. These accounts were coded by Radian and
included in the total of points evaluated, but not keypunched or
delivered on magnetic tapes. The TACB has the original coding
screens, which require additional input for completion.
• Accounts with insufficient information to code required data—all
major processes and associated emission points falling into this
category were returned to the TACB for coding.
Several code lists were referenced in this project to obtain additional
information for the coding screens. The most important one is the SCC (Source
Classification Code) list, which identifies a large number of process emission
sources by unique code numbers. Each code number has a required throughput
entry appropriate to the source, such as tons produced or million cubic feet
of fuel burned. Coding the SCC number and throughput for a source results in
computer-applied emission factors and an output of predicted emissions. On
some questionnaires actual stack measurements or other source parameters more
representative than SCC emission factors were available. In those cases, the
coder was able to override the above system and specify the actual nature and
quantity of pollutants emitted. The complete set of SCC listings is presented
in Appendix G.
Another important supplement was the Pollutant Code List, which lists
the most common air pollutants by a systematic code numbering system. An
alphabetical cross-reference list was also provided to aid in locating
specific pollutants by name. The numerical pollutant code list is given in
Appendix H.
Three other code lists also used are not included in appendices to this
report. The SIC (Standard Industrial Classification), IPP (Implementation
Planning Program), and Abatement Equipment code lists can be found in the
references mentioned in the introduction to Appendix D.
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SECTION 5
COMPUTERIZED DATA PROCESSING
After the TACB emissions inventory coding forms were checked for
errors, the data were keypunched. The punched cards for each complete account
of questionnaires were kept together as a group. Several of these groups were
then collected. The resulting collection of cards contained approximately
1500 cards (approximately one box). Each box of cards was then submitted to
the Edit and Reformat programs. In all, approximately 11 boxes of punched
cards were processed (approximately 18,000 cards). Appendix E presents the
keypunching instructions and Appendix F is a guide to the Edit and Reformat
programs.
Each box of cards was submitted to the Edit program for the identifica-
tion of obvious errors. The errors were corrected and the data were resub-
mitted to the Edit program. This cycle was repeated for each box of cards
until no further errors were identified.
After each box of cards was successfully processed by the Edit program,
the data were submitted to the Reformat program. The Reformat program read
the edited data, reformatted the data into the proper format for processing
by the TACB programs, and stored the reformatted data on a disk file. Then
the contents of the disk file were copied to a magnetic tape and delivered
to TACB for processing on their computer.
The TACB processing consisted of copying the contents of the magnetic
tape to a disk file followed by a review of the data. When errors were
detected, error reports were submitted to Radian, and the errors were cor-
rected by keypunching new corrected cards. Once again, the data were sub-
mitted to the Edit and Reformat programs, and a magnetic tape was produced
and delivered to TACB.
A total of 11 finalized magnetic tapes was delivered to TACB.
11
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12
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APPENDIX A
INSTRUCTIONS FOR EVALUATING
QUESTIONNAIRES
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Introduction
The 1975 TACB Emissions Inventory questionnaires are to be evaluated for
all sources in the Houston area emitting greater than 500 tons per year of
any criteria pollutant (particulates, S02, NO , CO, HC), for a minimum of 2000
emission points. Any point emitting more than 10 tons/year or 4 Ibs/hr of a
criteria pollutant will be entered into the data base. These general instruc-
tions are provided as a guide in evaluating the questionnaires.
General
The TACB has reviewed and verified data for NO and HC emissions
(Houston area SMSA) and particulate (Pa) emissions (Harris County only).
These data will be entered as listed without further evaluation on our part.
One exception is the category of power plants, which must be thoroughly
evaluated for NO emissions. For SOa and all other pollutants, Radian will
verify emissions data through calculation, material balance, use of emission
factors, and other methods; the company will be contacted only as a last resort.
Before examining the questionnaire, search the folder for additional
information the company may have sent, such as letters, stack tests, and
plant maps. The folder should also contain inspection reports by TACB
Regional staff which may clarify information in the questionnaire.
A work sheet should be filled out for each questionnaire, noting any
discrepancies in data, telephone contacts to companies, and especially
assumptions made during evaluation. Some points which emit less than a
certain cut-off limit or which are identified as confidential will not be
coded by Radian. Use the work sheet to list all emission points not coded,
and give the reason why. Before starting to evaluate the questionnaire,
locate the overall process flowsheet for the entire plant. If one is not
provided, look through the individual process flow diagrams. Find out the
raw materials used as process feed, how these materials are processed, and
what the finished product is. This will familiarize the coder with the basic
functions of the plant, as well as how the various processes are related.
Definitions
For the purpose of this project, a process is defined as an operation or
series of operations integral to a plant's functions. This exact listing of
processes varies from company to company, so as a general rule use the process
pages in the questionnaire as guidelines. An emission point is defined as
one or more operations or connected processes which result in a source of
emissions. For example, fluid catalytic cracking is a process within a
petroleum refinery. The primary emission point associated with this process
includes the cracking unit itself, a CO boiler (which is both a combustion
unit and abatement device), and an electrostatic precipitator (abatement'
device). Although the ESP stack is the ultimate source of emissions to the
atmosphere, all the units listed above comprise the emission point. Another
example is an industrial boiler, which is both a process and a single emis-
sion point. One process may have several emission points, but in other
cases several processes may constitute one emission point.
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Evaluation Instructions for Specific Questionnaire Pages
Page 1
Page 1 lists the company name and location, type of business, and primary
products. The top center of this page should indicate whether or not confi-
dential material has been removed. Contact the task leader if confidential
material is missing from the file, as the TACB will be reviewing all confi-
dential data for us.
Page 2
This page lists total fuel usage. In the case of unusual fuels for
which emission factors are not given, the TACB will furnish appropriate
information. Methane feed to a process may be listed on page 2 as a fuel
instead of on page 8 as process feed. Check both pages for consistency in
reporting. All boilers with heat input less than 1 MMBtu/hr should be grouped.
Page 9
All combustion sources are listed separately on page 9, and should be
correlated with the fuel usage on page 2. Add up the fuel consumed by
heaters, boilers, engines, and turbines on page 9. Comparison with the cor-
responding lines on page 2 should give agreement of fuel usage within 10%.
Page 13
This page gives a summary of total emissions in tons per year, broken
down by individual emission points. Questionnaires which have been evaluated
by the TACB should already identify most emission points by name. Check to
see if there are emission points on page 13 not listed on page 9 (combustion
sources). Looking down the columns for NOX and SOa emissions on page 13 could
give an indication of combustion sources not listed on page 9.
Page 11
Page 11 gives stream composition and stack data for each emission point.
SC-2 emission points should be checked to identify additional combustion
sources not listed on pages 2 or 9. Take the total flow rate in ACFM for
each stack, convert to SCFM using temperatures given, and compare with the
individual pollutant flow rates given in SCFM. If stack velocities or actual
flow rates are not provided by the company, use the following values:
19.99 ft/sec combustion stacks
39.99 ft/sec process stacks
Page 3
Waste disposal by combustion is listed on this page. Be observant for
processes such as flares or sulfur recovery units erroneously listed on this
15
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page. Auxiliary fuel consumed by incinerators may not be reported under
total fuel usage on page 2. In such a case, the auxiliary fuel input listed
on page 3 must be added to the other fuel given on page 9 in order to balance
total fuel usage. On the other hand, fuel usage listed on-page 2 may not be
given on page 3. Extensive cross-checking is the rule when evaluating
ques tionnaires.
Page 5
Loading and unloading information is given on this page. Disregard all
unloading operations, as the resultant emissions are reflected as tank
filling emissions which have already been accounted for in a previous study.
If an emission point is identified both as loading and unloading, assume
that all material is loaded. If both bottom and splash loading are indi-
cated, assume all splash loading. Reid vapor pressure values must be con-
verted to psia before coding.
Page 6
This page lists painting, printing, and degreasing operations. A mini-
mum size cutoff will be provided by the TACB for painting operations. If
the weight percent of solvent is not provided, assume 50% by weight. Use
a paint density of 10 Ibs/gal if none is furnished by the company.
Page 8
A separate page 8 is filled out by the company for each separate plant
process. Quantities of raw materials and products are listed, as well as
all associated emission points and control devices. An emission point may be
listed as part of a process on page 8 but not reported in the stack data on
page 11 or the emissions summary on page 13. Continue cross-checking until
all emission points associated with each process are identified. The
process flow diagram attached to each page 8 is very important in defining
flow relationships for each process. The network screen, to be discussed
in a separate set of coding instructions, transfers the schematic flow
diagram to a set of linear flow relationships. Therefore, the accuracy and
usefulness of the network screen are dependent on the coder's careful exami-
nation of all page 8 process flow diagrams.
Page 14
Due to the recent adoption of a Federal lead standard, the TACB wants
lead emissions coded. Any emission point numbers associated with lead
emissions should be noted on page 14. Cross-referencing to pages 8, 11 and
13 will provide sufficient information for coding.
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APPENDIX B
SAMPLE TEXAS AIR CONTROL BOARD
EMISSIONS INVENTORY QUESTIONNAIRE
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TEXAS AIR CONTROL BOARD PAGE - 1
EMISSIONS INVENTOR* QJEST 1 ONNA IKE ACCOUNT NO. -
NEDS/EMS NJ. -
ADDRESS CORRECTION BOX COUNTY -
REGION -
DESIRED MAILING ADDRESS ! MAILED -
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•
1 GROUP(S) -
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•
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•
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•
FACILITY LOCATION 1
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•
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•
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•
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00 _ _ _ _ _
FULL* COMPLETE AM!) RETURN THIS QUESTIONNAIRE FOR THE ABOVE CALENDAR YEAR rtlTHIN DAYS OF THE MAILING
DATE ro: EMISSIONS INVENTORY, TEXAS AIR CONTROL BOARD, 8b'^0 SHOAL CREEK BLVD., AUSTIN, TEXAS 7B7bd.
YJU ARE RESPONSIBLE FOR PROVIDING COMPLETE INFORMATION COVERING THE ABOVE CALENDAR YEAR, NO MATTER MAT
PjRt'lJ* OK THE YEAR YOU OPERATED AND/OR OdNED THE FACILITY, OR HOd SMALL YOUR SOURCE OK EMISSIONS.
FAILURE TO COMPLY MAY BE GROUNDS FOR THE INSTITUTION OF LEGAL PROCEEDINGS IN ACCORDANCE All TH THE
PROVISIONS OF SECTION 4.02 OF THE TEXAS CLEAN AIR ACT, rtHlCH PROVIDES FOR CIVIL PENALTIES OF SbO TO 51,000
PcJH VIOLATION AND PER DAY OF VIOLATION AND/OR INJUMCT1VE RELIEF.
YDU ARE RfciSPONSlBLE FOR THE PORTION OF THE YEAR YOU OPERATED, THIS FACILITY OPERATED TO _..
SPECIFIC BUSINESS: PRIMARY PRODUCTS: .
TELEPHONE: AREA CODE NUMBER .
NUMB£R OF EMPLOYEES AREA OF CONTIGUOUS PROPERTY (ACRES AND TENTHS) .
CHECK SHIFTS NOT WORKED: DAY _, EVENING .., NIGHT . ; MARK OUT DAYS NOT FORKED: S M T * T F S
MJMBtR OF DAYS OPERATING PER YEAR: .
PERCENT OF ANNUAL PRODUCTION BY SEASON: SPRING ', SUMMER , FALL , WINTER .
I HEREBY ATTEST THAT THE INFORMATION SUPPLIED HEREIN IS TRUE, CORRECT, AND COMPLETE
TO THE BEST OF MY KNOWLEDGE.
SIGNATURE AND TITLE OF AUTHORIZED REPKtSENTATI VE • TACti ACCOUNT NUMBER
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TEXAS AIR CONTROL BOARD
Emissions Inventory
Data For Year
Page 2
Account No.
TOTAL FUEL
Please indicate in the spaces below the total quantities and types of fuel consumed in your operations for the year indicated above. The fuels should be allocated in the
categories indicated. All combustion devices such as kilns, dryers, etc., must be indicated under OTHER (SPECIFY) in the column labeled TYPE OF UNIT. IN-PLANT
VEHICLES are considered as all vehicles whose use is confined to plant property and do not travel on public roads. These include fork-lifts, caterpillars, front-end
loaders, trucks, cars (confined to plant property), drag lines, etc. If you utilize any fuels that are not listed, you must indicate the type, quantity (include measured
units) and sulfur content of these fuels in the column labeled OTHER FUELS. The quantities of fuel indicated on this page must balance the sum of fuels indicated on
page 9, with the exception to the quantity indicated for IN-PLANT VEHICLES and SPACE HEATERS.
Type of Unit
Space Heaters
Process Heaters
Boilers
Stationary Engines
Stationary Turbines
In-Plant Vehicles
Other (specify)
Total Consumed
Natural Gas
(1000 Cubic Ft)
(MSCF)
Distillate Oil
(1000 Gal)
Wt
%
S
Residual Oil
(1000 Gal)
Wt
%
S
Gasoline
(1000 Gal)
Coal - Lignite
Specify
Type
CLOOO Tons)
Wt
a
7°
Ash
Wt
%
S
Other Fuels
Type, Quantities
And Units
Wt
%
S
PLEASE SUPPLY THE FOLLOWING PLANT INFORMATION
Center of Plant Location: : : (Degrees:Minutes:Seconds) North Latitude
(Degrees:Minutes:Seconds) Wesc Longitude
Average Plant Elevation Above Sea Level: (Feet)
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TEXAS AIR CONTROL BOARD
Emissions Inventory
Data For Year
Page 3
Account No.
WASTE DISPOSAL
Indicate combustion methods of all WASTE MATERIAL at this location. Name the type of waste burned with the heat content in Btu per specified units. When a
particular type of waste is a mixture, list the weight percent of each component in the mixture. Each combustion device must be designated by a specific EMISSION
POINT NUMBER as assigned on your plant lay-out map. These combustion units with their respective designated emission point numbers should be listed on both
tables of this page and also on pages 11 and 13. Enter the following COMBUSTION METHODS as they apply to your waste disposal in the tables below.
COMBUSTION METHODS
1. Open Burning
3. Multiple Chamber Incinerator
5. Other (Specify)
2. Single Chamber Incinerator
U. Conical Metal Burner
Emission
Point
Number
Combustion Method
Name or Type of Material
(Include Wt % of Mixtures)
Heat
Content
(Btu
Units)
Quantity Burned
Lb/Hr
Lb/Day
Tons/Yr
Burn Schedule
Hrs/Day
Days/Yr
N>
O
Emission
Point
Number
Inc inerator /Burner
(Manufacturer and Model Number)
Auxiliary Fuel
Type
(Specify)
Quantity Per
Year
(Specify Units)
" Pollution Control Equipment
Type of Control
Control
Number
Avg
Eff
(*)
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TEXAS AIR CONTROL BOARD
Emissions Inventory
Data For Year
Page U
Account No.
STORAGE TANK DATA
List all storage tanks greater than 1000 gallon capacity including crude petroleum and fuel oil. Exclude N2 and r^O vapor in your tonnage calculations. Enter
absolute vapor pressure at the,yearly average liquid storage temperature. Subtotal emissions on each page with a grand total on the last page. Refer to page 12
for Storage Tank loss summation.
Emission
Point
Number
Tank
Capacity
(1000 Gal)
Type Tank
(Fixed Roof)
(Float Roof)
(Pressure)
Material
Stored
-
Mol*
Wt
Net**
Monthly
Thru-Put
(1000 Gal)
-
Vapor
Pressure
PSIA @ °F
Control
Pressure
(PSIG)
* Use average molecular weight for mixtures.
Type
Vapor
Control
Avg
Eff
"(*)
Page Total
Vent
(Tons
Year)
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TEXAS AIR CONTROL BOARD
Emissions Inventory
Data For Year
Page 5
Account No,
LOADING AND UNLOADING
List all volatile compounds transferred including crude petroleum and fuel oil. Exclude ^ and r^O vapor in your tonnage calculations. Enter absolute
vapor pressure at the yearly average liquid temperature. Subtotal emissions on each page with a grand total on the last page. Refer to page 12 for Load-
ing • Unloading loss summation.
Emission
Point
Number
Type Transfer
(Cars, Trucks
Ships, Barges,
Pipe Line)
Load
Unload
Name
of
Material
Mol*
Wt
Monthly
Thru-Put
(1000 Gal)
Vapor
Pressure
PSIA g °F
-
Vapor
Recovery
Yes
No
Bottom
Loading
Yes
'Use average molecular weight for mixtures.
No
Splash
Loading
Yes
No
Page Total
Vapor
Loss
(Tons
Year)
to
N3
-------
TEXAS AIR CONTROL BOARD
Emissions Inventory
Data For Year
Page 6
Account No.
PAINTING, PRINTING AND DECREASING
List all PAINTING, PRINTING, SURFACE COATING and/or DECREASING operations including both maintenance and process use. Assign an EMISSION POINT
NUMBER for maintenance type painting, degreasing, etc. Also assign emission point numbers to each SPECIFIC PROCESS using these materials and complete a
separate page 8 for each process. These emission point numbers with their respective emissions must also be reported on pages 11 and 13. Include chemical analyses
of all materials on a separate page*
PAINTING, PRINTING OR OTHER SURFACE COATING
Emission
Point
Number
-
Type of Paint, Ink
or Solvent
(Describe)
Quantity
Used
(1000 Gal)
Density
(Lb/Gal)
Solvent
(wt %)
Emission Control Devices
Type
(Specify)
Avg
% Eff
Emissions
(Tons/Year)
CCt
Part
10
u>
DEGREASING OPERATIONS
Emission
Point
Number
Describe Degreasing
Agent Used
Quantity in 1000 Gal
Purchased
Repro-
cessed*
Density
(Lb/Gal)
Emission Control Devices
Type
(Specify)
Avg
% Eff
Emissions
(Tons /Year)
Carbon Compds . t
'Amount sold or returned for reprocessing.
tCarbon Compounds (Definition on page 12).
-------
TEXAS AIR CONTROL BOARD Page 7
EMISSIONS INVENTORY
PAGE 8 INSTRUCTIONS
A SEPARATE page 8 must be completed for each SPECIFIC PROCESS within your plant
location. Many final products are the result of several specific processes conducted in sequence;
each intermediate specific process requires the completion of a separate page 8.
All materials in the process feed and all products (substances produced) from the process along
with their corresponding quantities and measured units must be listed in the indicated columns.
These materials/substances should be listed by chemical name except when the common name
is more applicable. Do not over-simplify your entries. This information must reflect a complete
material balance.
Attach a process flow diagram to each page 8. This diagram must indicate the flow of materials
into, through and from the process; the equipment pertinent to the process; the emission points
and control devices. The equipment should be descriptively named and the emission points and
control devices must be indicated by number and name. This name should be descriptive as it
relates to the process, e.g., "sulfur recovery incinerator stack" rather than "stack", etc.
Assign an emission point number to Fugitive type losses for each specific process (refer to
Emission Point Type 7 on page 12). All emission point numbers with their respective quantity
of emissions must also be reported on pages 11 and 13.
Cost data for air pollution control equipment has been added to page 8. Energy Consumed is
the supplemental energy such as fuel, steam and/or electricity required to operate the control
equipment.
24
-------
TEXAS AIR CONTROL BOARD
Emissions Inventory
Data for Year
Page 8
Account No.
PROCESS DATA
Process Name or Description
Operating Rate: % of Maximum Capacity
Operating Schedule:.
List All Emission Point Numbers Associated With This Process
_Hours/Day.
_Days/Week.
Weeks/Year
PROCESS FEED/YEAR
PROCESS PRODUCT/YEAR
to
(Jl
Material
Quantity
Units
Material
Quantity
-
Units
Emission
Point
Number
Associated Air Pollution
Control Device
Control
Number
Pollutants
Controlled
i
Avg
%
Eff
Date
Installed
Total
Installed
Cost
Energy Consumed
(Specify Quantity
and Units)
-------
TEXAS AIR CONTROL BOARD
Emissions Inventory
Data For Year
Page 9
Account No.
HEAT. STEAM AND POWER
List all BOILERS, HEATERS (except space heaters). ENGINES and TURBINES (referred to as emission points) used for the production of heat, steam and/or
power in your operation. In-process combustion equipment such as process dryers, furnaces, kilns, etc.. should be listed as heaters on this page and should be
indicated on pages 8, 11 and 13. Use one line for each combustion unit (emission point) and identify each by a specific EMISSION POINT NUMBER as shown
on your plant layout map. These emission point numbers with their respective emissions must also be included on pages 11 and 13.
FOR BOILERS - SPECIFY TYPE OF FIRING AS TANGENTIAL, OPPOSED, FRONT, ETC.
Emission
Point
Number
Design Capacity of Each Unit
Boilers
Million
Btu/Hr
Heat
Input
Type
of
Firing
Heaters
Million
Btu/Hr
Heat
Input
Engines
Brake
Horse
Power
Turbines
Brake
Horse
Power
Fuel Data
Type .
(Specify)
Quantity Per
Year
(Specify Units)
Heat
Content
(Btu
Units)
Wt.
%
S
Pollution Control Equip.
Type
of
Control
Control
Number
V
g^~
Vl *HW.
QJ pq-_-
<;
-------
TEXAS AIR CONTROL BOARD Page 10
EMISSIONS INVENTORY
PAGE 11 INSTRUCTIONS
It is intended that all emissions except those from volatile storage and loading (Pages 4 and 5) be described in
this section including discharge parameters of a stack or vent where parameters exist.
1. Emission Point Number • Emission point numbers should be identical with the numbers on the flow sheets
and the remainder of the questionnaire. Combine fugitive emissions into one emission point number for
each specific process as listed on page 8.
2. Stream Composition
Component - Report all air contaminants regardless of concentration. Also report air, nitrogen,
carbon dioxide, and moisture as necessary to account for at least 95 percent of total stream volume.
Report components as specific chemicals. Do not use general terms like particulates, organics,
hydrocarbons, olefins, trade names, etc.
Molecular weight - Report the molecular weight of each air contaminant. It is not necessary to
report molecular weight of air, nitrogen, carbon dioxide and moisture.
Concentration • Report gaseous components in volume percent (mol %) and paniculate matter in
grains per standard cubic foot (70°F, 387 standard cubic feet per pound-mol).
3. Normal Flow Rate of Each Component - It is intended that the average flow rate of each component
during normal operation be reported in these two columns. Periods of idle plant operation are not to be
used in the calculation of normal flow rate.
Gas - Report the flow rate of each gaseous component in standard cubic feet per minute at 70°F.
Paniculate - Report the flow rate of each paniculate component in pounds per hour. Indicate the
weight percent of "Fine Particulates Less Than 5 Microns" in the space labeled "% Fines."
\ 4. Total Flow Rate - Report total flow rate of each component in tons per year taking into consideration the
total time of operation of the source during the calendar year. Do not report tons per year of air,
nitrogen, carbon dioxide and moisture components.
5. Latitude and Longitude - Report the latitude and longitude of the emission point to the nearest second.
For groups of emissions reported as one emission point number, report the latitude and longitude of a
point generally central to the group of emissions.
6. Stack or Vent Information • Do not leave blank except for fugitive emissions having no flue.
Height Above Ground • Report the height of stack or vent opening above ground level in feet.
Inside Diameter at Exit - Report the internal diameter of round stacks at the stack exit in feet.
Describe other than round vertical discharge points with dimensions and discharge direction.
Temperature • Report discharge temperature from the stack or vent in °F.
Velocity • Report the stack or vent exit velocity in feet per second. Enter (M) or (C) by each
velocity to indicate whether Measured or Calculated.
Total Flow Rate • Report the total stack or vent flow rate in cubic feet per minute at the discharge
temperature (ACFM) during normal operation.
Duplicate page 11 if necessary to list all emission points.
27
-------
TEXAS AIR CONTROL BOARD
Emissions Inventory
Data For Year
Page 11
Account No.
STREAM COMPOSITION AND STACK DATA
1
Emission
Point
Number
2
Stream Composition
Component
Mol
Wt
Cone-
3
Normal Flow Rate
of Each Component
Gas
SCFM
(70°F)
Particulate
Lb
Hr
%
Fines
1*
Total
Flow
Rate
(Tons
Year)
5
Latitude
Longitude
(To The
Nearest
Second)
6
Stack or Vent Information
Height
Above
Ground
(Ft)
Inside
Diam
At Exit
(Ft)
Temp
(°F)
~
Velocity
(Ft/Sec)
Total
Flow
Rate
(ACFM)
to
00
-------
TEXAS AIR CONTROL BOARD Page 12
EMISSIONS INVENTORY
PAGE 13 INSTRUCTIONS
List the emissions in tons per year for each emission point except Storage and Loading. These emission point
numbers must match those in your process flow diagrams and in other pages of this questionnaire.
Stream Composition and Stack Data (page 11) represents normal flow rates and these emissions should be recorded
on page 13. Additional emissions which have occurred from upset conditions, start-ups, shut-downs, abatement
equipment failure, purging, etc., should be listed separately on page 13 as a second line entry for each emission point.
Storage and Loading - Unloading should be sufficiently detailed on pages 4 and 5. An emission point number for
each tank and loading rack is not required on page 13. Pages 4 and 5 should have the emissions on each page
subtotaled with a grand total on the last page. The total emissions from pages 4 and 5 should be a two line
entry on page 13. These line entries should be labeled STG p. 4 and Ld p. 5.
Categorize each emission point into one of the following EMISSION POINT TYPES and indicate this in the
designated column. The proper CALCULATION METHOD CODE must be indicated in each pollutant column to
indicate your method of calculating each pollutant for each emission point. If you indicate the data is the result
of stack tests, you must include copies of these test results to substantiate your data. Make additional copies of
page 13 as necessary. Show subtotals on each page 13 and a grand total on the final page.
EMISSION POINT TYPES
1. Stack or Vent 2. Elevated Flare
3. Ground Flare 4. Open Dump
5. Incinerator 6. Tank
7. Fugitive Emissions (Loss from other than a flue and those listed in Type 8 below). Combine into one
emission point number for each specific process as listed on page 8.
8. Emissions from cooling towers, ponds, reservoirs, lagoons, basins, separators, or other containments except
tanks.
CALCULATION METHOD CODES
A. Stack Test (Attach copies)
B. Material Balance
C. Emission Factors (AP-42, 2nd Ed. + Supplements)
D. Estimate by Other Calculations
E. Guess (Use only as a last resort)
Example: 200 tons per year 862 by material balance.
Sulfur
Dioxide
200 B
Carbon Compds. Column - Include all carbon compounds as defined in Texas Air Control Board Rule No. 1.05
except carbon monoxide which should be listed separately.
H2S04 Column - Include 803 calculated as H2S04.
Other Column - Supply chemical composition and quantity in tons/year.
-------
TEXAS AIR CONTROL BOARD
Emissions Inventory
Data For Year
Page 13
Account No.
TOTAL EMISSIONS
Emission
Point
Number
Emission
Point
Type
Page Total
(Tons Per Year)
Nitrogen
Oxides
Sulfur
Dioxide
Carbon
Compds .
Carbon
Monoxide
Particu-
lates
H2S
H2SOij
Fluo-
rides
NH3
C12
HC1
Other
(Specify)
-------
TEXAS AIR CONTROL BOARD
Emissions Inventory
Data For Year
Page lU
Account No.
EMISSION CHECKLIST
List the Emission Point Number(s) for any of the following
elements or compounds containing them which may be
emitted to the atmosphere from your operation.
Emission
Point
Number
Antimony
Arsenic
Barium
Beryllium
Boron
Bromine
Cadmium
Chlorine
Chromium
Copper
Fluorine
Indium
Iodine -
Lead
Manganese
Mercury
Molybdenum
Nickel
Noble Metals
Rare Earths
Selenium
Tellurium
Thallium
Tin
Vanadium
Zinc
Other Heavy Metals,
List the Emission Point Number(s) for any of the following
substances or products containing them which may be
emitted to the atmosphere from your operation.
Emission
Point
Number
Aldehydes
Ammonia or Ammonia Compounds
Asbestos
Carbonyls
Chromic Acid.
Cyanide or Cyanide Compounds
Disulfides
Fluorocarbon Compounds
Halogenated Hydrocarbons
Herbicides
Mercaptans ,
Nitric Acid
Odor Causing Compounds ,
Organic Phosphate ,
Organics
Ozone ,
Pesticides
Phosphoric Acid ,
Polychlorinated Biphenyls (PCB),
Polynuclear Organics ,
Sulfides
Talc
Vinyl Chloride
Volatile Organic Solvents
Include emissions data for these sources on pages 8, 11 and 13.
-------
TEXAS AIR CONTROL BOARD
Emissions Inventory
Data For Year
Page 15
Account No.
FUTURE EMISSIONS
Estimate the future total emissions from this facility for the following calendar years in tons per year.
Year
1976
1977
1980
1985
Nitrogen
Oxides
Sulfur
Dioxide
Carbon
Corapds .
Carbon
Monoxide
Particu-
lates
H2S
H2SOU
Fluo-
rides
NH3
C12
HC1
Other
(Specify)
UJ
10
List emission point numbers of Heat, Steam and Power equipment (Page 9) indicating present and future conversion to alternate energy sources.
Energy Source
Coal (Specify Type)
Residual Oil
Distillate Oil
Electricity
Other (Specify)
Can Presently Use in Addition
to Fuel Specified on Page 9
Will Be Converted to Use This
Energy Source (Estimate Date)
-------
Groups 3 - 4 TEXAS AIR CONTROL BOARD Page 7
EMISSIONS INVENTORY
PAGE 8 INSTRUCTIONS
A SEPARATE page 8 must be completed for each SPECIFIC PROCESS within your plant location. Many final
products are the result of several specific processes conducted in sequence; each intermediate specific process
requires the completion of a separate page 8.
All materials in the process feed and all products {substances produced) from the process along with their
corresponding quantities and measured units must be listed in the indicated columns. These materials/substances
should be listed by chemical name except when the common name is more applicable. Do not over-simplify your
entries. This information must reflect a complete material balance.
Attach a process flow diagram to each page 8. This diagram must indicate the flow of materials into, through and
from the process; the equipment pertinent to the process; the emission points and control devices. The equipment
should be descriptively named and the emission points and control devices must be indicated by number and name.
This name should be descriptive as it relates to the process, e.g., "sulfur recovery incinerator stack" rather than
"stacFVetc.
Assign an emission point number to Fugitive type losses for each specific process (refer to Emission Point Type 7
on page 12). All emission point numbers with their respective quantity of emissions must also be reported on
pages 11 and 13.
Cost data for air pollution control equipment has been added to page 8. Energy Consumed is the supplemental
energy such as fuel, steam and/or electricity required to operate the control equipment.
Brick and Pottery Manufacturing and Related Products
SPECIFIC PROCESSES include: All types of raw material drying and/or calcining including sand, grinding,
kilns, storage, etc.
Raw Material Storage: Indicate whether raw materials are stored in a moist condition and also if they are
stored openly, partially enclosed, enclosed, or in bags.
Grinding: Indicate type of grinding (wet or dry) and controls.
33
-------
Group 5 TEXAS AIR CONTROL BOARD Page 7
EMISSIONS INVENTORY
PAGE 8 INSTRUCTIONS
A SEPARATE page 8 must be completed for each SPECIFIC PROCESS within your plant location. Many final
products are the result of several specific processes conducted in sequence; each intermediate specific process
requires the completion of a separate page 8.
All materials in the process feed and all products (substances produced) from the process along with their
corresponding quantities and measured units must be listed in the indicated columns. These materials/substances
should be listed by chemical name except when the common name is more applicable. Do not over-simplify your
entries. This information must reflect a complete material balance.
Attach a process flow diagram to each page 8. This diagram must indicate the flow of materials into, through and
from the process; the equipment pertinent to the process; the emission points and control devices. The equipment
should be descriptively named and the emission points and control devices must be indicated by number and name.
This name should be descriptive as it relates to the process, e.g., "sulfur recovery incinerator stack" rather than
"stacFTetc.
Assign an emission point number to Fugitive type losses for each specific process (refer to Emission Point Type 7
on page 12). All emission point numbers with their respective quantity of emissions must also be reported on
pages 11 and 13.
Cost data for air pollution control equipment has been added to page 8. Energy Consumed is the supplemental
energy such as fuel, steam and/or electricity required to operate the control equipment.
Carbon Black
SPECIFIC PROCESSES include: furnace operation, drying, packaging, etc. A separate page 8 and flow
diagram is required for each process.
The dryers should be indicated on the process flow diagram as direct or indirect fired.
Report carbon black produced from gas and oil as separate quantities and identify on page 8.
List weight percent sulfur in the process feed and provide a total sulfur balance over the process.
34
-------
Group 6 TEXAS AIR CONTROL BOARD Pag« 7
EMISSIONS INVENTORY
PAGE 8 INSTRUCTIONS
A SEPARATE page 8 must be completed for each SPECIFIC ^PROCESS within your plant location. Many final
products are the result of several specific processes conducted Tn sequence; each intermediate specific process
requires the completion of a separate page 8.
All materials in the process feed and all products (substances produced) from the process along with their
corresponding quantities and measured units must be listed in the indicated columns. These materials/substances
should be listed by chemical name except when the common name is more applicable. Do not over-simplify your
entries. This information must reflect a complete material balance.
Attach a process flow diagram to each page 8. This diagram must indicate the flow of materials into, through and
from the process; the equipment pertinent to the process; the emission points and control devices. The equipment
should be descriptively named and the emission points and control devices must be indicated by number and name.
This name should be descriptive as it relates to the process, e.g., "sulfur recovery incinerator stack" rather than
"stacFTetc. . fc
Assign an emission point number to Fugitive type losses for each specific process (refer to Emission Point Type 7
on page 12). All emission point numbers with their respective quantity .of emissions must also be reported on
pages 11 and 13.
Cost data for air pollution control equipment has been added to page 8. Energy Consumed is the supplemental
energy such as fuel, steam and/or electricity required to operate the control equipment.
Petroleum Refining
SPECIFIC PROCESSES include: crude distillation, vacuum distillation, catalytic (cracking, reforming,
alkylation, hydrogen treating, dehydrogenation, isomerization, polymerization), asphalt, coking, OEA/MEA
system, sulfur recovery, acid recovery, acid production, water separator, cooling tower, blowdown system,
waste water treatment, thermal process by type, other separate petrochemical operations, etc. A separate
page 8 and flow diagram is required for each process. .
Indicate type of unit as well as the name when more than one type of unit is generally available for a
particular process operation.
The number and type of catalytic conversion stages for sulfur recovery units should be indicated on the
process flow diagram. Enter page 8 data in sufficient detail to calculate percent sulfur recovered.
35
-------
36
-------
APPENDIX C
EMISSIONS INVENTORY
QUESTIONNAIRES CONTAINING
DATA NOT CODED
37
-------
APPENDIX C
1. Accounts partially coded by Radian, to be completed and keypunched by
TACB.
TAGS Account Number TACB Account Name
1. BL-0031-U Monsanto, Alvin
2. BL-0042-G Phillips Petroleum, Sweeny
3. GB-0001-R Amoco Chemicals, Texas City
4. GB-0028-U GAF Corp.
5. HG-0033-B ARCO Chemical
6. HG-0126-Q Celanese Chemical, Bayport
7. HG-0218-K DuPont
8. HG-0225-N Ethyl Corp.
9. HG-0232-Q Exxon, Baytown Refinery
10. HG-0537-0 Oxirane Chemical
11. HG-0558-G Pennwalt Corp.
12. HG-0562-P Petro-Tex Chemical
13. HG-0665-E Soltex Polymer
2. Accounts not coded by Radian, to be coded and keypunched totally by TACB.
TACB Account Number TACB Account Name
1. BL-0002-S Amoco Chemicals, Alvin
2. BL-0021-0 Dow-Badische
3. BL-0023-K Dow.Ch^rn., Oyster Creek. Div.
4. HG-0127-0 Celanese Chemical, Houston
5. HG-0618-N Reichold Chemical
6. HG-0715-0 Texaco, N. Houston Terminal
38
-------
APPENDIX D
INSTRUCTIONS FOR CODING 1975
EMISSIONS INVENTORY DATA
39
-------
TABLE OF CONTENTS
1.0 In troduc t ion
2.0 Code Lists
2.1 SCC
2.2 SIC
2.3 IPP
2.4 Pollutant
2.5 Abatement Equipment
3.0 Sequence Types
3.1 Sequences Associated with Stacks
4.0
3
.2
3.1.1
3.1.2
3.1.3
3.1.4
3.1.5
3.1.6
PR:
AB:
ST:
SG:
PF:
NT:
Sequences
3.2.1
3.2.2
3.2.3
3.2.4
3.2.5
FL:
FG:
LU:
LG:
FU:
Process
Abatement
Stack
Stack Group
Process Fugitive
Network
Not Associated with Stacks
Flare
Flare Group
Loading/Unloading
Loading Group
Miscellaneous Fugitive
Screens
4
4
4
4
4
4
4
4
4
4
4
4
4
4
4
.1
.2
.3
.4
.5
.6
.7
.8
.9
.10
.11
.12
.13
.14
.15
Screen
Screen
S creen
Screen
Screen
Screen
Screen
Screen
Screen
Screen
Screen
Screen
Screen
Screen
Screen
1:
0:
M:
A:
S:
F:
Z:
X:
K:
L:
R:
J:
C:
B:
N:
General Information
Process Description
Process Mode of Operation
Abatement/ Control Description
Stack Description
Flare Description
Flare or Flare Group Process Data
Flare Operation
Tank or Load/Unload
Loading/Unloading Physical Description
Mode of Operation for Tanks and
Group Area Description
Pollutant Information
Process Fugitive Description
Network
Loading/Unloading
40
-------
5.0 Coding Procedure
5.1 Identification Line
5.2 Numeric Field
5.3 Alphanumeric Field
5.4 Text Field
Table 1. Emission Cut-Offs
Table 2. Screen Summary Sheet
Table 3. Assumptions
41
-------
1.0 INTRODUCTION
This manual provides instructions for coding emissions data from the
1975 Texas Air Control Board Emissions Inventory questionnaires to generate a
computerized point source data base. Only those sources in Harris, Galveston,
and Brazoria Counties emitting more than 200 tons per year of SOa, NO , CO,
or HC, or more than 25 tons per year of particulate, are evaluated. Any point
emitting more than 10 tons per year or 4 pounds per hour is entered into the
data base. An exception to this rule occurs with smaller particulate
sources. Refer to Table 1, "Emission Cut-Offs," for the appropriate particu-
late cut-off values.
For the purposes of this project, all types of emission sources will be
coded except for storage tanks. Types of sources include processes, asso-
ciated abatement equipment, stacks, flares, loading, and fugitives.
Eleven (11) sequence types have been developed for coding these kinds of
sources. Section 3.0 describes the applications of each sequence type in
detail.
Information required for each sequence type is conveyed through the use
of "screens," which are actually hard-copy coding sheets rather than terminal
screens. There are 15 screens which, in various combinations, comprise the
sequence types. Section 4.0 of the manual provides complete instructions
for filling out each screen.
Certain screens require information which is best represented in code
form. Five major code lists are used: SCC, SIC, IPP, Pollutant, and
Abatement Equipment. SCC and Pollutant code lists are presented in Appendices
H and I, respectively. The other referenced lists are not included in this
manual but can be found in the following sources:
SIC - U.S. Office of Management and Budget. Standard Industrial
Classification Manual 1972. Government Printing Office,
Washington, D.C., 1972.
IPP - Environmental Protection Agency, Guide for Compiling a
Comprehensive Emissions Inventory, March 1973, Appendix A.4,
pp. A-37-42.
Abatement Equipment - Permits Data System PM05 User's Manual,
Appendix E, Texas Air Control Board, revised May 1975.
Refer to Section 2.0 for discussions of code lists.
In summary, the data coded are to be used for the following purposes:
1) Retrieval of information put into the system. The format of coded
data is suited for modeling studies, regulation development, and
other purposes.
42
-------
2) Tracking of emissions as they change over the years. The Radian
study furnishes the system with initial data, which will be augmented
by any future coding into the system.
43
-------
2.0 CODE LISTS
2.1 SCC (Source Classification Code)
The SCC table is a compilation of emission factors by source category.
Unlike with the AP-42 Emission Factors, however, the coder does not calcu-
late actual emissions by applying the factors. All that is required is to
enter the proper SCC number and certain process operating data for the
source as described below. Refer to Appendix H for a complete listing of
SCC numbers.
In this example, an industrial external combustion boiler of 125 MM Btu/hr
heat input, front firing, and burning No. 6 residual oil is to be coded.
Refer to the SCC table under 1-02-016-BZ, which identifies the process as
"External Combustion Boiler, Industrial, No. 6 Residual Oil, 100-250 MM Btu
Other." The SCC number is always located in the first column of every entry
and uniquely identifies the process in question. The second column con-
tains a descriptive title of the process. The next column contains process
throughput units which must be observed when entering data onto a screen.
In the present example, "1000 gallons burned" are the specified units. The
next two columns contain additional parameters which should be coded if
provided in the questionnaire.
The SCC heading immediately below the No. 6 Residual Oil example is
titled, "External Combustion Boiler, Industrial, Other/Not Classified," and
begins with 1-02-999-97. Note that the second column does not provide a
descriptive title; this must be specified in the coder's remarks. In
the third column specifying throughput units, asterisks appear beside each
of the entries. This means that emission factors do not exist for that SCC
number. In this situation, emissions data must be supplied by the coder
from any source (usually the questionnaire) considered reliable. This
approach is explained under the "C screen" discussion.
The "Other/Not Classified" category appears frequently throughout the
entire SCC list. Since this classification makes source identification dif-
ficult for data retrieval purposes, it should be used as a last resort only.
In the case of fuels, try to find an SCC classification similar to the fuel
of concern for which there is an emission factor. For process sources, con-
tact designated TACB personnel so that an appropriate SCC number may be
assigned. If the "Other/Not Classified" classification must be used, make
sure the "Comments" section on the appropriate screen describes the process
adequately.
A few SCC classifications request additional data, identified by "X
factor," located in the far right column of a given SCC entry. This informa-
tion must be entered to complete the necessary calculations by computer.
For example, the series beginning with the SCC number 4-02-001-01, "Point
Source Evaporation, Surface Coating, Paint," has an additional column titled
"X Factor = % Solvent." Enter this information onto the appropriate screen,
using data supplied from the questionnaire or other sources.
44
-------
2.2 SIC (Standard Industrial Classification)
In comparison to the SCC numbers, which specify process type, the SIC
system identifies products or services. A plant may have multiple SIC codes
associated with its operations. For example, in a plant conducting both
natural gas processing and sulfur recovery process heaters would be identi-
fied by the respective SIC code of the process being served.
2.3 IFF (Implementation Planning Program)
The IPP codes provide more detailed information about certain processes
within a given SIC code. IPP codes are always used in conjunction with SIC
codes.
Any boiler, no matter what its SIC code, must be assigned an IPP combus-
tion code number. The last page of the IPP list provides combustion code
numbers. Since these codes deal almost exclusively with coal-fired combus-
tion units, and the boilers in this study usually burn only gaseous and
liquid fuels, "00, All not listed," will be used most commonly for boilers.
Note that heaters, engines, turbines, incinerators, or other combustion
devices are not coded under the IPP system unless specifically provided for.
The IPP list gives SIC headings, under which various processes relating
to the SIC type are listed. For an FCCU in a petroleum refinery, for example,
both the SIC code (2911) and IPP code (01) are needed to completely describe
the process.
2.4 Pollutant Codes
The pollutant code table is a listing of compounds, compound groups,
and other materials by means of 5-digit codes. An alphabetical listing is
also available for cross-reference. Refer to Appendix I for a listing of
pollutant codes by numerical order. Only the second column, giving the
pollutant identification number, and the third column, giving a descriptive
title, are used. Codes below 10000 (the first six on the list) will not be
used.
The series starting with 10000 contains types of particulate. Particu-
late is uniquely identified by a "1" as the first digit. Note that the more
non-zero digits appearing in the 5-digit code, the more specialized the
description of the pollutant, whereas more zeros imply a more generalized
description. Use the most specific description possible. For example, the
most general code for particulate is 10000—particulate, unspecified.
Progressively more detailed codes are
11000 - particulate, chemical, unspecified;
11100.- ammonium compound, unspecified; and
11105 - ammonium chloride.
Note that nitric acid (11165), sulfuric acid (11175), and other condensed
inorganic acids are listed as particulate.
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The series starting with 50000 contains types of organic compounds and
materials. If sufficient information is not given to determine whether or
not an organic pollutant contains methane, use code 50000—methane or VOC
(volatile organic compound), unspecified. If, however, it is known that the
organic pollutant does not contain methane, use code 50001—nonmethane VOC,
unspecified. Methane (60000) is given a unique code number separate from
the other organic pollutants.
The 70000 series lists inorganic gases, 80000 is reserved for ozone
alone, and the 90000 series contains two code entries, C02 and CO. The last
code number is 99999, for odor, and should not be used.
There are several codes available for pesticides, depending on physical
state and composition. Code numbers 11300 through 11800 are for pesticide
particulate. Code numbers 58900 through 58960 are for gaseous organic
pesticides, and numbers 71000 through 71300 are for gaseous inorganic pesti-
cides.
A letter appearing after the 5-digit pollutant code means that the
pollutant may be identified by more than one name. For example, ethylene
dichloride (53270), ethylene chloride (53270A) and 1, 2-dichloroethane (53270B)
are equivalent names for the same compound. The letters are not coded onto
the forms, but only serve to distinguish different terms for a given pollutant.
If the appropriate pollutant code cannot be located on this list, contact
designated TACB personnel so that one can be assigned.
2.5 Abatement Equipment Codes
The abatement equipment code list provides standard abatement devices
used in air pollution control, arranged by category and type. Each section
heading is given a code, as well as the more detailed sub-headings below it.
For example, if a scrubber is employed as an abatement device but detailed
information is not furnished, code 270 for "Scrubbers-Miscellaneous Types."
If a Venturi scrubber is specifically mentioned but the degree of efficiency
is not, code 260 by the same principle.
The columns farthest to the right on this list give efficiency range
and normal efficiency, both in percent. These figures may be used in the
absence of more reliable data. Many questionnaires routinely list 99.9%
control efficiencies for all abatement devices, regardless of the type of
equipment and its application. Compare the efficiencies on this table to
those listed in the questionnaires, being alert for serious discrepancies.
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3.0 SEQUENCE TYPES
Eleven (11) sequence types have been developed to code the various
types of sources encountered in the questionnaires. This section explains
each sequence type, its applications, and limitations. The discussion of
sequence types is divided into two parts: sequences associated with
stacks and sequences not associated with stacks. Sequence types of the
first kind are related to one another by means of a network.
3.1 Sequences Associated with Stacks
3.1.1 PR-Process
Screens: 1, 0, M
Only those types of processes with stacks as final emission points are
to be coded under the PR sequence. As a general rule, each process listed
on a separate Page 8 of the Emissions Inventory questionnaire will be coded
as a distinct PR sequence. Combustion devices such as boilers, heaters,
engines and turbines are considered processes unto themselves, regardless
of other processes they may be serving. Each process coded under a PR
sequence should relate to one unique SCC number. If more than one SCC
number seems appropriate, make new PR sequences until each has only one
SCC number. An exception to this rule is multiple fuels, to be discussed
later.
Processes may be grouped under the following conditions:
1) The individual process size or rated capacity is under a given cut-
off, but combined the group meets or exceeds the cut-off;
2) Emissions from the individual process fall below a given cut-off,
but combined the group meets or exceeds the cut-off;
3) All processes within a grouping must have the same SCC number.
3.1.2 AB-Abatement
Screens: 1, A
The AB sequence is used to code one or more abatement devices which
control a process. Any abatement device found on the abatement code list
may be represented as a control for a process with the exception of flares.
Although a flare may in actual practice be used to burn combustible streams
from a process, the abatement code for flare may not be used in conjunction
with a PR sequence. The waste gas flare is a separate sequence type, and
will be discussed later. The only valid use of the flare as an abatement
device occurs with the loading sequences, also to be discussed later.
47
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3.1.3 ST-Stack
Screens: 1, S, C
The ST sequence represents the final emission point of a process to the
atmosphere through a stack. Emissions discharged through a horizontal
opening or roof vent are also coded under the ST sequence. For purposes of
dispersion modeling, two or more identical stacks within a 30 ft. diameter
circle may be coded as one ST sequence. More detailed instructions for this
procedure are given under the discussion of the S screen, Section 4.5.
3.1.4 SG Sequence-Stack Group
Screens: 1, S, J, C
In some cases it is useful to group two or more stacks under the SG
sequence. Stacks should be grouped only if
1) They serve similar processes, have identical parameters, but lie
outside a 30 ft. diameter circle, or
2) Emissions from individual stacks fall below a pre-determined cut-off
and grouping is the only way to include them.
Note that the only difference between the ST and SG sequence is the presence
of a J screen for the latter sequence. Screen J, "Group Area Description,"
is discussed later in Section 4.12. The SG sequence is used when the group
of stacks covers more than a 30 ft. diameter circle in area.
3.1.5 PF sequence-Process Fugitive
Screens: 1, B, C
The PF sequence is used to account for fugitive emissions from any
process for which a stack has been coded, following the instructions for ST
or SG sequences. Relief valves, compressor seals, and blowdown systems are
some examples of fugitive emissions which may be coded under the PF sequence,
provided a coded stack is associated with the related process. The same
examples of fugitive emissions listed above are not coded as PF sequences if:
1) The process generating fugitive emissions is otherwise a closed
system with no stacks, or
2) Stack emissions from the process in question fall below a pre-
determined cut-off even with grouping, and are thus not coded as ST or SG
sequences.
In the case of (2) above, if process fugitives are large, it is advisable
to code stacks, no matter how small their emissions. The advantage of this
approach is that the PF sequence relates to a specific process, thus better
48
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characterizing fugitive emissions coming from the process. If there are no
stacks to code, the only way to account for fugitive emissions is to use the
FU sequence, "miscellaneous fugitives." The FU sequence is discussed in
Section 3.2.5.
3.1.6 NT Sequence-Network
Screens: 1, N
The NT sequence relates the process, abatement, stack, and process fugi-
tive sequences in a linear flow pattern. The network thus formed does not
necessarily represent links of material or air flow, but of pollutant flow.
The most typical network entry is illustrated below:
PR-1
1U02
- AH 1
100%
CT 1
o I J.
Process Abatement S tack
This information would be coded onto the N (Network) screen as follows:
A Percent Flow B Percent Flow C
Percent Flow
(A-B/B)
1. P R - 1 100
Percent Flow
(B-C/C)
AB-1 100 ST-1
The percent flow column between A and B tells what percent of its total flow
B receives from A. The flow relationship between B and C is represented in
the same way. In this case B (AB-1) receives 100% of its flow from A (PR-1),
and C (ST-1) receives 100% of its flow from B (AB-1). If the percent flow
columns are left blank, the system automatically assumes 100%. The percent
flow relationships are critical when volume units (ppm, ppb, or volume %)
are coded onto C screens for the stacks in question. Otherwise, the percent
flow information can be estimated if not readily obtainable from question-
naire data.
Several variations in the basic flow relationship of PR-AB-ST will be pre-
sented.
(a) Flow relationship longer than one line
The arrangement shown below,
| PR-11—| AB-1 |—I AB-2 I—I AB-3J—\ AB-4
runs over tiie- 3 columns provided per line. The relationship is
carried over to following lines in such a manner:
1.
2.
3.
A
P_ R -
*
"3T ~~ _
B
A 1 ~ I
A 1 ~ 1
ST-1
C
A1 - 1
AB-4
49
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An asterisk in the first character space implies the 'last type number
on the previous line. In the illustration above, the asterisk in the first
space of line 2 represents AB-2 of the previous line; likewise, the asterisk
in line 3 represents AB-4 in line 2. This is simply a shorthand method of
carrying a flow relationship over to one or more lines. The percent flow
columns have been left blank, assuming 100% flow from one sequence to the
next. A maximum of seven (7) items may be linked for any one straight net-
work chain. If there are more than seven links, two or more of the inter-
mediate abatement devices must be grouped into a single AB-sequence, so that
the total number of AB-sequences in the chain does not exceed five (5).
(b) One process to two stacks
100%
100%
is represented as
1.
2.
A
R - 1
S T - 2
A set of ditto marks in the first character space of any column implies the
type-number above it on the previous line. The ditto marks in the first space
of line 2 represent PR-1, which appears in the column immediately above. Note
that Stack 1 and Stack 2 each receive 100% of their flow from Process 1, and
the percent flow column between A and B is left blank.
(c) Two processes to two stacks
Two cement kilns exhausting to a single ESP and then to two stacks
would be represented as
1.
2.
and on the network screen,
A
Z 1 ~ i 50 A 1
PR-2 50 ::_
C
S_T_ - I
S T - 2
50
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(d) Multiple process, abatements, and stacks
Flow relationships in petrochemical plants can be quite complicated.
The example below illustrates variations typically encountered:
1.
2.
3.
4.
5.
A
Z 1 ~
P_ R -
it _
11 ~
it
B
A JJ - 1
ii _
II ~ 1
A! ~ !
P F -' 3
C
~
s"r - 4"
Note that the PF sequence, "process fugitive," is entered onto the network
as if it were a stack.
(e) Devices acting as both abatement and process.
Devices such as CO boilers, sulfur recovery units, and waste
incinerators are unique in the network because they function both
as abatement devices (removing one or more pollutants from the
stream) and as processes (using fuel, thus adding combustion
products to the stream). These devices are coded both as PR and
AB sequences in the following manner:
1.
2.
A
P_ R - I
P R - 2
90
B
A Jl - 1
S T - 1
10
C
S T - 1
Note that ST-1 receives 10%' of its flow from the abatement device (AB-1) and
90% of its flow from the process (PR-2). As indicated in the schematic
diagram, the representation within the dashed lines is physically one unit
51
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which serves two functions. The division of flow between these separate
functions is usually not provided in the questionnaire. This information
can be obtained, however, from the total flow rate through the device and
the amount of fuel consumed when the device functions as a process. The
AP-40 Air Pollution Engineering Manual gives flow rates of products of com-
bustion for various fuels and percent excess air. Unless otherwise pro-
vided, assume 15-20% excess air. A flow rate resulting only from fuel
combustion will be obtained. This figure divided by the total flow rate
gives the percent flow from the process. The process percent flow subtracted
from 100 gives the abatement percent flow.
There cannot be more than one link from a process to a stack. In the
following diagram,
AB-1
ST-1
AB-2
ST-2
there are two separate links:
PR-1
and PR-1
to
to
AB-1
AB-2
to
to
ST-1
ST-2.
This is a valid operation in the network. However, in this diagram,
PR-1
there are two links from PR-1 to ST-1, one through AB-1 and one through AB-2.
This configuration is not allowed in the network. In such a case the two
abatement devices should be grouped into one AB sequence, AB-1, 2.
When coding has been completed for an entire account, place the NT
sequence at the end of all PR, AB, PF, ST, and SG sequences. This is very
important since the computer starts calculations as soon as it encounters
the NT sequence.
3.2 Sequences Not Associated With Stacks
3.2.1 FL-Flare
Screens: 1, Z, F, X, C
Flares are unique in the coding system because they function both as
processes and final emission points. They are not considered as either PR
or ST sequences, and consequently are not part of the network sequence.
As discussed under the ST sequence previously, a flare which is used to abate
emissions from a process is not coded as an abatement device or stack. Since
there is no link between a flare and the process which it serves, the system
52.
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is totally dependent upon proper data entry onto the F screen ("Flare
Description"), discussed in Section 4.6
3.2.2 FG-Flare Group
Screens: 1, Z, F, J, X, C
The flare group (FG) sequence is the same as the flare (FL) sequence
with the addition of the J screen. Two or more flares may be grouped if:
1) The flares lie outside a circle of 30 ft. diameter; and
2) Emissions from individual flares fall below a pre-determined cut-
off and grouping is the only way to include them.
If the flares are within a 30 ft. diameter circle, code as a FL (flare)
rather than FG (flare group) sequence. In such a case, the emissions are
not spread over great enough an area for the area description to be mean-
ingful.
3.2.3 LU-Loading/Unloading
Only loading operations will be coded into the system, since the emis-
sions from unloading are reflected as tank filling emissions which are already
accounted for. It is important that all loading stations entered into a LU
sequence have the same SCC number. For example, truck and ship loading must
be coded as separate LU sequences since the SCC numbers are different.
Submerged truck loading and splash truck loading must be entered as separate
LU sequences for the same reason.
3.2.4 . Loading Group
Screens: 1, K. L. J. R, C, A
Loading stations spread over a greater area than a 30 ft. diameter circle
should be grouped under the LG sequence. The LG sequence is the same as the
LU sequence with the addition of the J screen. Otherwise, the same rules
given for coding the LU sequence apply to the LG sequence.
3.2.5 FU-Miscellaneous Fugitive
Screens: 1, 0, J, M, C, A
The FU sequence is used to code fugitive emissions which do not result
from processes with stacks. Such type of fugitives as open storage piles,
solvent and paint application, cooling towers, API separators, pump and
compressor seals, and motor vehicle emissions are included in this category.
Because of the relatively small size of individual fugitives and large area
over which they are spread, most FU sequences are considered as grouped emis-
sion points. It is possible, however, for large, well-defined fugitive
emission points such as cooling towers and storage piles to be coded
separately.
53
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For example, if two large storage piles are located at opposite ends
of a plant, each having emissions over the coding cut-off, they should be
coded separately and not grouped. On the other hand, if the piles are close
together (within 30 feet), or if each has emissions less than the coding
cut-off, they should be grouped. The key factor in grouping fugitive emis-
sions is deciding whether the sources in question can reasonably be called
a single emission point for modeling purposes.
Fugitive emissions which are grouped must all have the same SCC number.
In the case of in-plant vehicles fueled by gasoline, diesel and LPG, three
separate FU sequences must be filled out since each fuel listed has a
unique SCC number.
Certain categories of sources must always have FU sequences filled out.
With petroleum refineries, for example, the "Miscellaneous" SCC heading
beginning with 3-06-008-01 lists five sources of fugitives within a refinery.
The refinery capacity in thousands of barrels is entered for each of the five
fugitive types, and the appropriate emissions are calculated by computer.
Another example involves compressor fugitives within a natural gas processing
plant. The SCC number (3-10-002-AD) is entered, plant throughput in MMscf
processed is entered, and fugitive emissions are automatically calculated.
54
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4.0 SCREENS
There are 15 screens or coding forms, onto which the sequence types are
coded. Refer to Table 2, "Screen Summary Sheet," for a listing of screens
required for each sequence type. Not all of the designated screens will
be used to complete a sequence type in some cases, but those that are used
must follow the order given in the table. An arrow beside a screen letter
means that the screen is loopable—that is, multiple screens of the same
type may be entered under a single sequence type. Applications of looping
will be discussed under the appropriate screen type.
4.1 Screen 1; General Information
'£he 1 screen relates certain identifying information and is the first
screen entry for all 15 sequence types.
Date Coded: The order of dates is year/month/day, so that June 1,
1979 would be coded 79/06/01.
Responsibility Code: This identifies the coder preparing the forms by
initials. A person with initials "ABC" would fill in
ABC1-RA. The last two letters, RA, identify Radian. For
only two initials, code AB01-RA.
Account Number: All TACB account numbers follow the format of 2 letters
(county identifier), 4 digits, and 1 letter. Example:
HG-0048-L.
Sequence Type: Fill in the sequence type being coded. This entry will
always be two letters.
Identifying Number: This identifies the particular process, stack, flares,
etc. being coded, and should follow the company's own
numbering system as closely as possible. Up to 8 spaces
are available for letters, numbers, or punctuations, but
blank spaces are not valid entries. For grouped points,
use the following notation:
1/4 1 through 4
1,4 1 and 4
1-4 not used
If the sequence type is NT (network), use the identifying
number of the first process entered on line 1 of the NT
screen.
Record Serial Number: Code 0^ of ^ in most cases.
There are situations where the production methods, operat-
ing characteristics, or emissions of processes, abatement
55
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devices or stacks change significantly during the year to
new modes of operation. In these cases a distinct record
serial number is assigned to each new configuration. The
sequence type in question is coded as many times as neces-
sary to represent all new modes of operation.
For example, a process which operates continuously
through 1975 has a stack which is uncontrolled until mid-
year 1975. At that time an abatement device is installed
which drastically changes the stack's emissions. The 1
screen for the process (PR) sequence has a record serial
number 01 of 01, since the process itself does not change
production rates or schedules. The stack (ST) sequence
is coded twice. The 1 screen for the first ST sequence
(uncontrolled) has a record serial number 01 of 02, whereas
the 1 screen for the second ST sequence (controlled) is
coded 02 of 02. The abatement device installed at mid-
year is coded as an AB (abatement) sequence. Its 1 screen
has a record serial number 01 of 01.
Note that only major physical changes in operations
are assigned new record serial numbers. A process which
merely increases or decreases throughput at a certain
time of year is not coded as two distinct record serial
numbers. However, if the process changes to a new produc-
tion method involving different reactants and emission
rates (and possibly a change in SCC number), a separate
record serial number is assigned to the modified process.
SIC, IPP: Note that SIC and/or IPP numbers are entered only for those
sequence types containing 0, K, or Z screens.
Record Applicable Time Period: This entry records the time period during
which any configuration (process, stack, or other sequence
type) operates as coded. The most common entry will be
75/01/01 THRU 99/12/31. If an abatement scheme goes into
effect on June 1, 1975, code as follows: 75/06/01 THRU
99/12/31. If a process shuts down December 31, 1975, code
as follows: 75/01/01 THRU 75/12/31.
The instructions given above for record serial coordi-
nate closely with the record applicable time period.
Note that any information filled out below the follow-
ing line on the screen will be disregarded if the sequence
type is ST, SG, PF, AB, or NT. However, for the remaining
sequence types, comments may be provided at the bottom of
the form, 3 lines of 48 spaces each.
Permit Number: Disregard
56
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NSPS, NESHAPS, TOXIC SUBSTANCE, ODOR: Place a "Y" for "yes" in the
appropriate space if any of these descriptive categories
apply.
PSD Analysis Required: Disregard.
PSD Increment Affected: Disregard.
Offset Required: Disregard.
Section Codes: Disregard
4.2 Screen 0; Process Description
The 0 screen is used under the PR and FU sequences to convey process
information.
Number of Similar Processes: Enter 1 for a single process, or the
appropriate number for grouped processes.
Primary SCC: Enter the proper SCC number.
Confidential: Fill in a "C" in this space if confidential material
is being evaluated.
Process Name: This should be a brief descriptive title such as
"Boiler" or "FCCU," or name of a process such as
"Aromatics Recovery" or "In-plant Vehicles." Twenty-
four (24) spaces are available for process name.
Design (Rated) Operating Rate: This applies mainly to boilers and other
combustion devices. The first space on this line is
reserved for a numerical entry, followed by units (see list
of units and corresponding number codes on the 0 screen)
and time (H for hour, D for day). For example, a boiler
rated at 250 MM Btu/hr would be entered as 250 9_ PER H.
Leave the design operating rate space blank if it is not
provided.
Maximum Operating Rate: Assume 100% if not provided. If the question-
(% of Design) naire gives a figure greater than 100% for
maximum operating rate, use the company's figure.
Annual Throughput: The list of units with corresponding number codes
is to be used here. This space may be left blank if the
throughput is entered in the same units as the process SCC
number. In the space following "1975" on the following
line, enter the appropriate throughput, making sure that
this number corresponds to the units entered on the pre-
vious line.
57
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Feed or Fuel WT% SULFUR, FUEL WT% ASH, FUEL WT NITROGEN: Enter these
if provided by the questionnaire. If data are not pro-
vided, do not enter 0 (zero), but leave them blank.
X Factor: This is an extra entry required by some SCC numbers. Refer
to the discussion of SCC numbers under Section 2.1. Be
sure to fill this space if it is part of the required
information, since the computer will not supply this
value into a blank space.
Heat Content: The first blank on this line is for a numerical entry,
and the second blank gives MBTU per units chosen from the
list entitled "Heat Content Units." For example, natural
gas with a heat content of 1030 Btu/scf could be entered
either as 1030 IN MBTU/UNITS: _4
or 1.030 IN MBTU/UNITS: 12_
Comments: Forty-eight (48) spaces are available at the bottom of the
0 screen for entering additional information.
Applications of the 0 Screen
Whenever processes are grouped, it is important to enter the average
design operating rate and annual throughput, because .these values are
multiplied by the "number of similar processes" entered. Weighted average
values should also be entered for fuel weight percent constituents, X
factors, and heat content when grouping is done, although these values are
not multiplied by number of similar processes.
As an example of grouping in the FU (miscellaneous fugitive) sequence,
suppose there are 2 storage files next to each other which are being con-
sidered as a single emission point. The coder has the option of putting a
"2" in "number of similar processes," and the annual throughput (tons material
stored) for one process, or putting a "1" in "number of similar processes,"
and the annual throughput for both processes combined. Since throughput is
multiplied times number of similar processes, these two methods of coding
are equivalent.
Alternate Fuels
In the case of boilers, heaters, and other combustion units using
multiple fuels, fill out a separate 0 screen for each fuel. There will be
a unique SCC number for each fuel.
A special case of alternate fuel is auxiliary fuel used by gaseous,
liquid, or solid waste incinerators. Under the SCC headings for each of
these types of incinerators locate "Auxiliary Fuel." This section contains
SCC numbers for most commonly used fuels. If the incinerator functions as
an abatement device by removing one or more pollutants from the stream, code
the auxiliary fuel usage as a separate process as described in Section 3.1.6
58
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under "Network Sequence." If the incinerator merely serves to reduce the
volume of solid waste and does not function as an abatement device, two 0
screens are filled out. The first 0 screen accounts for emissions from the
incineration of waste material, and the second 0 screen accounts for fuel
combustion emissions. Appropriate SCC numbers are entered onto each of the
0 screens.
In-Process Fuels
There are a number of processes such as kilns, dryers and furnaces
which generate emissions unique to the process itself in addition to emis-
sions from fuel combustion. Moreover, both types of emissions are mixed at
the point of exit to the atmosphere. One or more fuels which serve such a
process are termed "in-process fuels." There are special SCC numbers to be
used for in-process fuels, beginning with the 3-90 series.
For example, if a cement kiln (wet process) fired by natural gas were
being coded, the following 0 screens with indicated SCC numbers would be
filled out within one PR sequence:
1. 3-05-007-04 Kilns—gas fired
2. 3-90-006-02 Cement kiln/dryer in-process fuel
4.3 Screen M; Process Mode of Operation
The M screen is used in the PR and FU sequences to relate operational
data concerning a process.
Year of Record: File in 1975.
Operating rate may be coded as 1) hourly/daily/weekly or
2) seasonal, day/night.
1) The first option will be used almost exclusively for coding operat-
ing rates. Operating rate (percent of design capacity):
This may be found, at the top of each process page in the El ques-
tionnaire. For boilers, operating rate will be automatically calcu-
lated by computer, provided design (rated) operating rate and annual
throughput are furnished on the 0 screen. For heaters, engines, and
turbines, put the operating rate of the process being served. If no
information is provided on the El process page concerning operating
rate, assume 85% for production processes.
Operating Schedule: This should also be provided at the top of each
process page in the El questionnaire. If not provided,
assume 24 hr/day, 7 day/wk, 52 wk/yr.
59
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2) The second option for coding operating rates applies strictly to
seasonal or day/night shift operations. This type of information is usually
not furnished except by agricultural sources.
If the operating rate and operating schedule spaces are left blank,
values automatically default to 100% and 24/7/52. Thus, the M screen may
be omitted if these parameters already apply to the process in question and
the annual throughput was entered on the 0 screen. The M screen is likewise
not needed if a boiler runs continuously and the operating rate is to be
calculated from parameters already entered on the 0 screen. However, it is
important to note that partially filled blanks are not acceptable; either
all or none of the blanks are to be coded. If a boiler has an operating
schedule other than 24/7/52, thus requiring information to be entered in
these spaces, then the operating rate must also be filled in. Operating rate
for a boiler is calculated by dividing the actual fuel consumed, in MM Btu/hr,
by the rated capacity of the boiler in MM Btu/hr.
Both the 0 and M screens are loopable; that is, multiple, sets may be
entered if more than one fuel is used. In actual practice, most question-
naires do not provide separate operating schedules for each type of fuel.
In these cases be sure that the annual throughput is entered on the 0 screen
for each SCC and omit the M screens.
Some judgments may have to be made on the part of the coder with regard
to operating schedules not furnished in the questionnaire. Maintenance
painting, for example, might reasonably be assigned an operating schedule
of 8 hr/day, 5 day/wk 52 wk/yr. In cases which are not particularly well
suited to M screen coding, such as fugitives, assign the operating parameters
of a key plant process. As before, omission of the M screen defaults
values to 100% and 24/7/52. This approach is acceptable if no further
information is available.
4.4 Screen A; Abatement/Control Description
The A screen comprises the AB sequence and can also be added to LU, LG
and FU sequences.
Number of Similar Abatement Devices: Enter the appropriate number of
similar abatement devices which form a continuous link
from process to stack.
Abatement Code: Select the proper code from the Abatement Equipment
Code List.
Description: Forty (40) spaces are available if the abatement code alone
is not sufficient to properly define the abatement device.
Unit Size: Fill in this information if provided and if appropriate for
the abatement device being coded. The first blank on this
line is for a numerical entry, the second denotes "A" for
60
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ACFM or "S" for SCFM, and the third blank is for tempera-
ture in degrees Fahrenheit. A typical entry might look
like this:
UNIT SIZE
30
(1000 A CFM) @ 200 DEC F
Energy Used:
The first set of blanks is for a numerical entry. The
"E" stands for exponent. The second blank is for units;
enter the proper number code from the list provided on
the screen. For example, an abatement device consuming
630,000 KW hr/yr would be coded as
ENERGY USED
J3 £ E £ _5 (UNITS 3) .
Efficiencies: This is an important part of the A screen since emissions
generated from the PR sequence will be diminished by spe-
cific pollutant based on the efficiencies coded here. One
or more pollutants can be abated on one A screen, as long
as the corresponding percent efficiency is entered for
each pollutant. The first line contains the five criterion
pollutants, so that percent efficiency is all that is needed
in these blanks. For additional controlled pollutants,
list pollutant code and efficiency under "Other Pollutants."
Use average efficiency if several similar abatement devices
are entered on the A screen. If the efficiency is not pro-
vided in the questionnaire or appears to be too high,
obtain typical efficiency values from the Abatement Equip-
- ment Code List, AP-40 or AP-42 manuals, using the mid-
range of published values.
4.5 Screen S: Stack Description
Stack parameters are entered onto the S screen for both ST and SG
sequences.
Number of Similar Stacks: Code the proper number of stacks comprising
the ST or SG sequence. As discussed under the ST
sequence, two or more identical stacks within a 30 ft.
diameter circle may be coded as one ST sequence. Enter
the number of identical stacks in this space.
Location: UTM coordinates are the preferred choice if provided. Least
desirable but acceptable is a single latitude-longitude
coordinate for the center of the plant. If stacks are
grouped, 'average the coordinates to obtain a center point
coordinate.
61
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Stack Height: Enter from stack page in El questionnaire. Use average
stack height if stacks are grouped.
GEP Stack Height: Disregard.
Exit: Diameter: For a round stack, enter diameter in feet. For a
rectangular stack, use the "diameter" space for one dimen-
sion, and use the "rect" space for the other dimension.
For grouped stacks, use average diameter.
Stack Parameters at % Design Capacity: Enter the same percent design
capacity as the process which the stack serves. If a
valid stack test is included in the questionnaire, use
the value given in the stack test.
Temperature: Enter in degrees Fahrenheit, using average temperature
for grouped stacks.
Non-Linear Factor: Disregard.
Exit Velocity: Enter velocity in feet per second. If only flow rate
is given, code in the space following, indicating "A" or
"S" for ACFM or SCFM, respectively. Velocity is prefer-
able to flow rate if both are given. Disregard NON-LINEAR
FACTOR.
Moisture Content (volume percent): Enter from stack data page in El
questionnaire or stack test.
Horizontal Discharge, Roof Vent: Mark an X in the appropriate space
if either of these descriptions apply. A stack is defined
as a roof vent if it projects less than 10 ft. above the
height of the building.
Adjacent Structure Description: This information is not typically pro-
vided in the questionnaire. If it is, enter height, length
and width of a structure adjacent to the stack being coded.
Long Axis Orientation: The diagram below illustrates an adjacent
structure with north-south reference:
62
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This would be coded as 45 DEGREES 15 OF NORTH. Consult the
company plot plan to determine long axis orientation.
Stack to Structure Distance: Enter this distance in feet.
If none of the information concerning adjacent structure
is provided, disregard this part of the screen.
4.6 Screen F; Flare Description
The F screen is the key entry under the FL and FG sequences. Although
much of the information required for the F screen is not usually furnished
in the 1975 El questionnaires, certain assumptions will be provided here.
Also see Table 3, "Assumptions."
Location: UTM coordinates are the preferred choice if provided.
Least desirable but acceptable is a single latitude-longitude
coordinate for the center of the plant. If flares are
grouped, enter average coordinates for the center of the
group.
Flare Height: Enter from stack page in El questionnaire. Use average
flare height if flares are grouped.
Flare Diameter: Enter flare diameter in feet. Use average diameter
if flares are grouped.
Number of Similar Flares: Code the proper number of flares comprising
the FL or FG sequence. Two or more flares within a 30 ft.
diameter circle may be coded as one FL sequence. Enter
the number of grouped flares in this space.
Design Flow Rate: Enter the flow rate from the stack data page of the
questionnaire. If velocity is also given, it is prefer-
able to calculate flow rate from flare velocity and diameter.
If neither flow rate nor velocity is given, use 150 ft.
for velocity and calculate the flow rate. The second blank
on this line receives an "A" or "S" for ACFM or SCFM,
respectively. The third blank is for temperature in degrees
Fahrenheit. It is important that the temperature of the
incoming stream before flare combustion be entered here.
However, since the 1975 El questionnaire did not request
this information, practically all temperature data for flares
are post-combustion values. If the El gives a flare
temperature greater than 500°F, this is probably a post-
combustion temperature. Substitute 100°F for the flare
temperature in these cases.
63
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Stream
Content, Cla Content: Enter these values if provided, using
whichever code is appropriate.
Major Combustible Stream Components: Space is provided for entering
up to 5 stream components. Pollutant codes for commonly-
used compounds are listed at the bottom of this screen.
Note that NOX, SC-2, and other final emission products are
not to be entered here. For each stream component, enter
the flow (filling in either "A" or "S" for ACFM or SCFM) ,
molecular weight, and lower heating value in Btu/scf . If
stream components are not provided in the questionnaire,
use the following figures:
Comments:
Compound Code
Flow at Design
Molecular Weight
Lower Heating Value
50000
ACFM (same as flare
design flow)
50
3000
There are spaces for listing up to 5 stream components.
If more than 5 components are present, list the 4 largest
constituents then group the remainder on line 5, using
average parameters.
Forty-eight (48) spaces are reserved at the bottom of the
F screen for comments.
4.7 Screen Z; Flare or Flare Group Process Data
Primary SCC: There are presently two SCC numbers for flares. 3-01-900-99'
identifies waste gas flares from chemical manufacturing
processes, and 3-06-900-99 identifies waste gas flares from
petroleum industry processes.
Confidential: Fill in a "C" in this space if confidential material is
being evaluated.
Total Annual Gas Flow Through Flare or Flare Group: Calculate the total
yearly flow in millions of cubic feet, entering "A" for
ACFM or "S" for SCFM. The same temperature coded on the
F screen should be entered here. The space to the right
of "1975" is for the numerical entry. If flares are
grouped, this should be an average value.
4.8 Screen X; Flare Operation
This screen is the counterpart to the M screen for process mode of
operation. The general instructions given for coding of the M screen also
apply to the X screen.
64
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Year of Record: Fill in 1975.
Operating Rate (% of Design Flow). Use 100% if flow rate for stream
components was assumed equal to flare design flow rate.
Otherwise, assign the same percent operating rate as the
process which the flare serves.
Operating Schedule: Assume 24/7/52 if not provided in the question-
naire.
4.9 Screen K; Tank or Load/Unload Process Data
The K screen is the key entry under the LU and LG sequences.
SCC: Enter the appropriate SCC number describing both loading vehicle
(tank cars/trucks, ships, ocean barges, or barges) and
type of loading (submerged or splash). Unless otherwise
specified, enter the code for normal dedicated service
under each SCC heading. All loading points described on
a single K screen must fit the characteristics defined by
this SCC number.
Maximum Expected Throughput: Enter the monthly throughput from the
load/unloading page of the El questionnaire. There are
two choices for units. A blank in the units space denotes
thousands of gallons (MGAL), whereas .a "5" denotes thousands
of barrels (MBBL). The throughput figure must be an
average value if several loading stations are grouped.
Liquid Composition Data: Compound Code: A list of commonly loaded fuels
and other materials is provided at the bottom of the K
screen. Enter the appropriate pollutant code from this
list or from the master list for the compound being loaded.
There are spaces for listing up to 6 compounds or materials
loaded. If more space is needed, start another LU or LG
sequence, or fill in the first 5 lines and group the remain-
ing materials in line 6.
Volume % of Throughput: Divide the monthly throughput for each compound
loaded by "Maximum Expected Throughput" entered earlier
and multiply by 100. The volume percent throughput column
should add up to 100.
Liquid Vapor Pressure (psia). The vapor pressures listed in the El
questionnaire may be used, although caution is advised.
If vapor pressure tables are consulted, assume ambient
operating temperatures unless specified otherwise.
Liquid Molecular Weight: Enter molecular weight of compound or best
estimate for polymers, residues, etc.
' 65
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Liquid Density: This information is not usually provided in the El ques-
tionnaire, and must be obtained from density tables. Enter
"A" for API or "P" for pounds/gallon under the column
titled "Density Units."
4.10 Screen L: Loading/Unloading Physical Description;
Number of Similar Loading Stations: Enter the appropriate number of
stations in this space. Note that one station can load
several materials. Apply the rules for grouping, discussed
under the LU and LG sequences, to determine the proper number
of loading stations to be coded.
Location: UTM coordinates are preferred, but latitude-longitude coordi-
nates may be used if UTM figures are not provided. Use
average coordinates if stations are grouped.
Average Emissions Height (ft): Enter 20 in this blank; as a general
rule, average emissions height for loading operations is
not provided in the questionnaire.
Comments: Forty-eight (48) spaces are available for comments.
4.11 Screen R; Mode of Operation for Tanks and Loading/Unloading
The R screen is the equivalent of the M screen for processes and the
X screen for flares. If information requested on this screen has already
been entered on previous screens in the LU or LG sequence, the R screen may
be omitted.
Year of Record: Enter _7 _5 in this space.
Throughput Units: Leave blank for thousands of gallons (MGAL), or place
a "5" for thousands of barrels (MBBL).
Average Monthly Throughput: There is a choice of entering 1) monthly or
yearly throughput or 2) seasonal throughput.
1) The first option will be used almost exclusively for loading opera-
tions. Enter average monthly throughput (the same value coded on the K
screen under "Maximum Expected Throughput"). In the "Schedule" space enter
the number of months per year loading operations were conducted. This space
left blank will automatically default to "12." If an annual rather than
monthly throughput has been entered in the previous space, code a "99" in
the "Schedule" space to denote annual throughput.
2) The second option is used for loading operations which vary on a
seasonal basis. Enter the average monthly throughput per season, (1, 2, or
3) in the next column.
66
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4.12 Screen J: Group Area Description
The J screen is necessary whenever emissions are spread over a larger
area than a point source. It appears in the SG, FG, LG, and FU sequences.
The plot plan furnished with the El questionnaire will be useful in obtain-
ing data for the- J screen.
Area Dimensions: Fill in the length and width of the area containing
emissions being coded. If the exact location of the emis-
sions cannot be determined (as with fugitives, for example),
assume that the emissions are spread over the entire plant
or an appropriate part of the plant. When estimates are
made, fill in the same dimensions for width as for length,
thus making the area a square. The cover page of the El
questionnaire gives total plant acreage. This can be con-
verted to square dimensions in feet and used for the J
screen. This procedure is preferred for such fugitives
as in-plant vehicles and miscellaneous leaks.
Vertical Thickness of Emissions: This refers to the vertical band
through which emissions spread when first discharged.
diagram below shows five stacks:
The
Vert
of E
Vertical Thickness
The vertical thickness of emissions is the difference in
height between the highest and lowest stack. .A grouping
of stacks with identical heights would have a.vertical emis-
sions thickness of zero.
Area Long Axis Orientation: Refer to the explanation of this procedure
under the discussion of the S screen, Section 4.5. Instead
of an adjacent structure, the element of interest is the
area occupied by grouped stacks or fugitive emissions.
Suppose the stacks previously illustrated have the fol-
lowing configuration when viewed from above:
67
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f
The Area Long Axis Orientation space would be filled in
as DEGREES &) W OF NORTH.
4.13 Screen C; Pollutant Information
The discussion of SCC numbers outlined a procedure whereby a code is
entered for a given process, an emission factor corresponding to this code
is applied to a specified parameter such as process throughput, and emissions
are generated. These emissions may be reduced by means of abatement equip-
ment, and are finally discharged to the atmosphere. The C screen enables
the coder to override this system by specifying the exact nature and quantity
of pollutants emitted.
Since the information on the C screen takes priority over any other emis-
sions data generated from SCC numbers, it is important to note the proper
usage of this screen. For sources with established emission factors, such
as boilers and FCCU's, C screens should not be coded unless a valid stack
test (either company, contractor, or TACB) is attached to the questionnaire.
The stack test should be used only if it accurately reflects the rate and
schedule of operation for 1975.
In some cases SCC emission factors are too general to adequately char-
acterize emissions from a complex process. For example, the unique configura-
tion and composition of vent streams in a chemical process plant usually
preclude a single emission factor from accurately representing all the emis-
sions generated. It is therefore best to code major stacks within a chemical
process, entering C screens for each pollutant and each stack. Judgment must
be used on a case-by-case basis to determine whether C screens are needed
for a given stack, and also whether data supplied in the El questionnaire
are reliable enough to be used.
Another situation requiring a C screen is the absence of an emission
factor, denoted by an asterisk beside the SCC units on the master SCC list.
This is common for many chemical manufacturing and metallurgical processes,
as well as most fugitives. The SCC number is entered on the 0 screen as if
an emission factor existed, and C screens are required to represent emis-
sions from these processes.
68
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Specific entries on the C screen will be discussed in the order of their
appearance on the screen.
SCC: This is to be filled in for in-process or alternate fuels.
Process Number: For C screens entered under ST, SG or PF sequences,
code the corresponding process identifying number here.
Pollutant Code: Enter the appropriate code for the pollutant being
coded, using the most specific code available.
Molecular Weight: This entry is automatically entered by computer for
specific compounds with set molecular weights. For "un-
specified" pollutant codes and other pollutants whose
molecular weight would not be readily discernable, fill
in this space. This requirement is most important when
ppm, ppb, or volume percent units are used farther down
on the C screen.
Pollutant Name: The pollutant code previously entered identifies the
pollutant, but this space may be used to further char-
acterize the pollutant if necessary.
Particulate .% Fines: This information, if provided, will be found on
the stack data page of the El questionnaire.
Stack or Process Average: This space is for grouped emission points
only. Since average emission rates are entered on the
C screen, the number of grouped processes or stacks are
multiplied by the average emission to give total emissions.
Enter "S" for stack or "p" for process.
Emissions at % of Design Capacity: This number should correspond to
the percent design capacity of the process generating
emissions.
Uncontrolled/Controlled: The next two lines are for entry of the pol-
lutant emission rate, controlled and uncontrolled. The
first space of each is for a numerical entry, the second
space is for units (see code list at bottom of screen) and
the third space is for estimation method (see letter code
list on C screen). The emission units should be entered
as closely to measured units as possible. For example,
Ib/hr or ppm are preferred to tons/yr for stack emissions,
but tons/yr is usually most appropriate for fugitive emis-
sions. The letter codes for method of estimation have some
correlation to the codes supplied on the emissions summary
page of the El questionnaire. As an example, a stack test
69
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measuring 40 Ibs/hr of a pollutant (uncontrolled) would
be coded the following way:
UNCONTROLLED 4£ UNITS I EST METHOD M
Allowable: Disregard
Non-linear Factor: Disregard
Permit Special Provision Number: Disregard
Applicable NSPS: Disregard.
Applicable NESHAPS: A C screen which codes any pollutant regulated
by National Emission Standards for Hazardous Air Pollu-
tants (NESHAPS) must have this information supplied.
Refer to the NESHAPS regulations and locate the specific
paragraph which gives an emission standard for the pollu-
tant in question. For example, asbestos emitted from the
manufacture of cement products would be coded as
PARAGRAPH 61. 0. 1 1 (£) (2).
A list of commonly used pollutant codes is provided at the bottom of
the C screen for convenience.
Lead emissions are to be coded on C screens because of the promulgation
of a Federal lead standard. In many cases the exact quantity of lead emitted
is not provided in the questionnaire, and only "trace" amounts may be claimed.
In cases such as these, code lead onto a C screen for the process or stack
in question, leaving the "units" space blank and filling in an "N" (for nil)
in the estimation method space. Since the code for lead begins with "1,"
the particulate identifier, the lead emission rate overrides all other par-
ticulate calculated by emission factors. To prevent this from happening,
a second C screen should be entered with the general code for particulate
and an "F" (for factor) in the estimation method space.
4.14 Screen B; Process Fugitive Description
The B screen is the key entry in the PF sequence.
Fugitive SCC Number: A unique SCC number applying to process fugitive
emissions should be supplied in this space.
How are uncontrolled emissions to be calculated?
The next three lines give an option as to the method of
calculating process fugitive emissions.
ENTERED ON FOLLOWING SCREENS: This is the most common
method, in which one or more C screens are entered under
70
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the PF sequence to identify emissions. In most cases
they will be values obtained from the El questionnaire.
Place an "X" in the following space if applicable.
SCC Factor Multiplied by Process Thruput: Process fugitive emissions
may be obtained by multiplying the process throughput given
on the 0 screen of the PR sequence by an SCC factor. If
this is the case, place an "X" in the following space.
SCC Factor Multiplied By Some Other Parameter: It may be useful to
multiply the process fugitive SCC factor by some parameter
other than process throughput. For example, a process
with certain known operating variables may have an SCC
factor which is multiplied by the value of the variable
rather than by process throughput. If this is the case,
fill in the value of this variable in the indicated space.
Location: Process fugitive emissions can usually be assigned only to
general areas within a plant, or perhaps to the entire
plant. Estimate the coordinates of the center of the area
in question if the questionnaire does not provide the loca-
tion. As with other coordinate entries, UTM coordinates
are preferable to latitude-longitude if provided.
Average Emissions Height: Estimate the average height at which fugitives
are emitted. Twenty (20) ft., may be used if sufficient
information is not furnished.
Area Dimensions: Use the procedure outlined under discussion of area
dimensions in the J screen.
Vertical Thickness of Emissions: The discussion under "J screen" applies
here. Zero (0) may be used if sufficient information is
not furnished.
Long Axis Orientation: The same instructions given under discussion
of the S and J screens are to be followed. Since fugitives
emissions are generally spread over a large undefined area,
the long axis orientation spaces may be left blank.
Comments: Forty-eight (48) spaces are provided for comments.
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4.15 Screen N; Network
The first entry on line 1 of the network screen must be a PR sequence.
Each subsequent PR sequence must be entered on a new line. The N screen is
loopable, which means that additional screens may be added to continue coding
the network. If more than one N screen is used, line 1 of all subsequent
screens must be left blank. A flow sequence cannot be interrupted in order
to continue onto a subsequent N screen. The flow sequence must be coded in
its entirety on the following N screen rather than break up the flow sequence
between two N screens.
Any time that a process, abatement device, or stack is assigned more
than one record serial number, the network containing those sequence types
must also be given corresponding record serial numbers and record applicable
time periods. In the example given under the 1 screen discussion, the stack
changes from uncontrolled to controlled operating conditions at mid-year.
Two separate network sequences are needed to properly code this stack. The
1 screen for the first NT sequence is assigned a record serial number 01 of
02, and the record applicable time period reflects the total uncontrolled
operating time. The 1 screen for the second NT sequence is given 02 of 02
for record serial number, and the record applicable time period reflects the
total controlled operating time.
72
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5.0 CODING PROCEDURE
The purpose of this appendix is to explain the coding rules needed to
enter point source emission data on the Radian batch coding forms. The 15
coding forms are shown in Appendix B. The general form is identical to the
TACB interactive data entry system screens. However, when using the coding
forms, the data fields must be coded properly for the computer programs to
process the data correctly.
Upon completion of coding, the forms are delivered to keypunch operators
for punching. Since the data are punched directly from these forms, there
are symbols on the forms which are meaningful to the keypunch operators but
are not meaningful to coders.
5 .1 Identification Line
Each coding form can have up to four different types of data fields which
are to be filled in by the coder. As an example, refer to screen A. At the
top of screen A is an identification line with three items which are to be
filled in by the coder, but will not be keypunched. All screens with the
exception of screen 1 contain identification lines. The data coded on
identification lines are identical to certain fields coded on screen 1.
Any arbitrary screen can thus be identified and kept with the proper stack
of forms.
5.2 Numeric Field
The second type of data field is a numeric field. An example is shown
on the second line of Screen A beside the heading "Number of Similar Abate-
ment Devices". This type of field can be identified by the symbol j >3>,
The number (in this case, 3) indicates to the coder the maximum number of
digits to be coded in the field. The coder may code less than the maximum
number of digits. In the example, the following are proper entries: 1, 1.,
1.2, .01, etc.
5.3 Alphanumeric Field
An example of the third type of data field is shown on the left half
of the third line of screen A beside the heading "Abatement Code." This is
an alphanumeric field and it can be identified by the symbol | | | |.
Each sub-box of this field may be coded with a single character. In the cur-
rent example, three characters may be coded. Valid examples may include:
"ABC", "AC", "BC", "AB", etc. Note that for this type of field, a blank is
a significant character. Data will be punched exactly as coded, including
spaces, hyphens, etc.
5.4 Text Field
The fourth type of data field is the text field. An example is shown
on the right half of the third line of screen A. This type of field can be
73
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identified by the symbol | |40_J. ^e number preceding the backward
L is the maximum number of characters that may be coded in the field. In
this example, up to 40 characters may be coded in the field labeled "Description",
Any meaningful descriptive data, including punctuation and special char-
acters, may be entered by the coder.
74
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Table 1. Emission Cut-Offs
Type of Source
S02, NOX, HC, or CO:
Entire plant
Individual point sources
Particulate:
Entire plant
Individual point sources
Boilers, heaters, furnaces,
gasoline-powered reciprocating
engines
Turbines, internal combustion
engines fired by natural gas,
fuel gas, diesel oil
Incinerators
In-plant vehicles:
Gasoline
LPG
Diesel, distillate oil
Spaceheaters, natural gas fired
Paint booths
Load ing op era t ions:
Gasoline
Non-gasoline
Cut-Off
(not to be coded
if below this value)
200 Tons/yr
10 Tons/yr or 4 Ib/hr
25 Tons/yr
10% of annual emission rate
up to 100 Tons/yr
Then 10 Tons/yr or
4 Ib/hr for annual emission
rate >_ 100 Tons/yr
3 MM Btu/hr
1 MM Btu/hr
50 MM Btu/hr
5,000 gal/yr
9,500 gal/yr
42,500 gal/yr
165 MM scf/yr
10 gal/day
Throughput (M gal/mo.) x
v.p. (psia)=350
Throughput (M gal/mo.) x
v.p. (psia)=550
75
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TABLE 2. SCREEN SUMMARY SHEET
Processes with Stacks*
Flares
Loading
Misc.
Fugitive
PR
1
? o
CM
..
AB
1
A
PF
1
B
r c
ST
1
S
? c
SG
1
S
J
tc
NT
1
r N
FL
1
Z
F
t x
t c
FG
1
Z
F
J
Tx
t c
LU
1
K
L
? R
rc
A
LG
1
K
L
J
CR
? c
A
FU
1
0
J
?M
^ c
A
'
*The NT sequence must be used with any of these entries.
C denotes a loopable screen.
-------
Table 3. Assumptions (to be used
if data not provided)
Stack ht., ft.
Temp., °F
Velocity, ft/sec
Stack flow, acfm
Stack diameter, ft.
Boilers, Heaters
Engines
50 30
600 750
19.99 19.99
Calculate from molar combustion
volumes (AP-40)
Calculate from flow rate and velocity
Velocity, ft/sec
Flow rate, acfm
Temp., °F
Compound Code
Molecular Wt.
Lower heating value, Btu/scf
Paint density, Ib/gal
Solvent weight %
Flares
150
Calculate from
velocity and diameter
100
50000
50
3000
10
50
77
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78
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APPENDIX E
KEYPUNCHING INSTRUCTIONS FOR
EMISSIONS INVENTORY CODING FORMS
79
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CORPORATION
INTRODUCTION
The purpose of this document is to explain in detail
the proper manner of keypunching the Radian point source emis-
sions inventory coding forms. The forms were developed during
the performance of the contract in which Radian assisted the
Texas Air Control Board to evalute and organize a point source
emissions inventory in the Houston, Texas, region.
A total of 15 different coding forms was developed.
These coding forms were designed to be as similar as possible to
the TACB interactive data entry system CRT screens. Though the
forms may be confusing at first glance, they are laid out in a
systematic manner. This discussion will explain the proper
manner of keypunching from these coding forms and will point out
any areas likely to cause problems or confusion.
GENERAL INSTRUCTIONS
An example of each of the 15 coding forms is shown
in Appendix A. Note that each coding form is labeled as a screen
(e.g., SCREEN 1, SCREEN A, SCREEN B, etc.). In the discussion
that follows, the forms are referred to as their Screen designa-
tions .
All Screens, with the exception of Screen 1, contain
one or two lines at the top which are not keypunched. These
lines are used by the coders for identification purposes. The
data fields are labeled "Responsibility," "Account Number," and
"SEQ Type-Number." On several screens, two additional fields
labeled "SIC Code" and "IPP Code" are present in the identifica-
tion lines. Note, however, that Screen 1 does not contain an
identification line. All data on Screen 1 are keypunched.
80
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CORPORATION
Each 'screen can produce from 1 to 13 punched cards,
depending on the screen type and depending on whether data have
been coded on the forms. Note that horizontal dashed lines are
printed across each form. These dashed lines are aides to key-
punch operators in that they identify the beginning and ending
of each punched card. As an example, refer to Screen A. A maxi-
mum of 4 cards can be produced from each Screen A.
All punched cards are divided into 8 fields of 10
characters each. All data items punched on the card are left
justified within each field and blank filled on the right.
Occasionally, a data field may-be longer than 10 characters.
However, when this occurs, it is the last field of a card.
There are four types of data fields on each coding
form. Again, refer to Screen A which contains examples of each
type. The first data field of each card, columns 1-3, contains
a 3-character code which identifies the card. Examples are:
"A01," "A02," "K06," etc. On all cards, columns 4 through 10
are always blank.
The remaining three types of data field may be
categorized as numeric data, alphabetic data, and text. Card
A01 contains examples of all three types.
\
The numeric type can be identified by the symbol
| >3> . The number indicates the maximum number of digits
which may be coded in the field. For the case on card A01, up
to 3 digits may be coded. The data are punched starting in
column 11, left justified, and blank filled on the right.
The second type of data field (alphanumeric) can be
identified by the symbol I I I I . For this type of data field,
81
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CORPORATION
all characters are significant and must be punched exactly as
coded, including spaces and special characters. In the example
on card A01, the three characters are punched in columns 21-23.
The third type of data field is the text field and can
be identified by the symbol | [ 40 [ . The number indi-
cates the maximum number of characters which may be coded in the
field. In the example on card A01, up to 40 characters may be
coded and will be punched starting in column 31 of the card. At
the end of the text field, the card is completed (as indicated
by the *) and keypunching may begin on the next card.
Usually a single data field is punched in a single
10-character field. However, there are some exceptions which
are clearly indicated on the screens. Due to space constraints,
some data fields are punched together (or concatenated) in a
single card field. Also, on occasion data fields are read
vertically and the corresponding data items are concatenated in
a single field.
DETAILED SCREEN DISCUSSIONS
Screen 1 contains examples of concatenation both
horizontally and vertically. On card 101, note that the two
data fields "Sequence Type" and "Identifying Number" are con-
catenated in columns 41-50. On the same card, the four
data fields on the line beginning "Record Serial Number" are
concatenated in columns 51-60. On card 102, note that the
four data items on the line beginning "NSPS?" are punched in
columns 21-24. Also on the same card, note the vertical orienta-
tion of the six columns labeled "PA," "S02," "VOC," "NOX," "CO," and
"PB." All other data items of Screen 1 are punched in individual
card fields.
82
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CORPORATION
In Screen A, all data fields are punched in individual
card fields. In card A03, note the data field titled "Energy
Used." The thick vertical tic mark is an aid for the data coder
and indicates a decimal point. It must not" be keypunched.. _Like-
wise, the letter "E" of this data field must not be keypunched.
Screen B contains two occurrences of concatenated data
items. On card B01, two data items are concatenated in columns
21-22. Also on the same card, VERTICAL UTM and UTM ZONE FIELDS
are concatenated in columns 71-79. As discussed for Screen A,
the thick tic marks representing decimal points are not to be
keypunched.
Screen C contains two occurrences of concatenated data
items, both on card C04.
Screen F contains a single case of concatenated items
on card F02.
Screen K may produce up to seven punched cards. Note
that after the first card, each screen line will produce one
punched card. Horizontal dashed lines do not separate these
cards.
Screen L contains one case of concatenated data items
on card L01.
Screen M contains one case of concatenated data items
on card M01.
Screen N can produce up to 13 punched cards. Note
that the cards are not separated by horizontal dashed lines.
83
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CORPORATION
Screen R will produce a single pinched card. Two data
fields are concatenated in columns 11-15. Note that there are
two parts to screen R labeled 1 and 2. The coder will either
code the two data fields labeled 1 or he will code the eight data
fields under the label 2. If part 2 is coded, then the letter X
must be punched in column 75. If the coder fills out part 1, then
the letter X must not be punched in column 75.
Screen S contains one case of concatenated data items
in card SOI.
Screen X contains one case of concatenated data items
in card X01.
Screen Z contains a single case of concatenated data
items in card Z01.
84
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APPENDIX F
PROGRAMMER'S GUIDE TO THE
EDIT AND REFORMAT PROGRAMS
85
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TABLE OF CONTENTS
1.0 INTRODUCTION
2.0 EDIT PROGRAM
2.0.1 Data Reformatting
2.0.2 Inputs and Outputs
2.0.3 Processing
2.1 Main Program: RESCREEN
2.2 Screen Subroutines
2.2.1 Subroutine SCRN1
2.2.2 The Remaining Screen-Checking Subroutines
2.3 UTILITY Subroutines
2.3.1 Subroutine ACCOUNT
2.3.2 Subroutine OPENB
2.3.3 Subroutine ACNUMCK
2.3.4 Subroutine CONVERT
2.3.5 Subroutine SEQUENCE
2.3.6 Subroutine DEGF
2.3.7 Subroutine ERROR
2.3.8 Subroutine RJUST
2.3.9 Subroutine SHIFT
2.3.10 Subroutine CHANGE
3.0 REFORMAT PROGRAM
3.1 Main Program: REFORMAT
3.2 UTILITY Subroutines
3.3.1 OPENC
3.3.2 REF
3.3.3 SCR
86
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1.0 INTRODUCTION
The purpose of this appendix is to provide an overview of the data
processing system which was developed to complete this project. This discus-
sion is intended to serve as a guide to programmers who must implement and/or
modify the programs.
The data processing system consists of two computer programs: (1) The
Edit program and (2) the Reformat program. The Edit program reads punched
cards containing emission data, checks for validity, and produces a report of
errors and a disk file for further processing. The Reformat program then
reads the disk file and produces a new disk file containing all of the emis-
sions data in the proper input format for further processing by TACB programs.
87
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2.0 EDIT PROGRAM
The purpose of the Edit program is to read the cards which were keypunched
from the emissions inventory coding forms, check for errors, and write those
cards containing no errors to a disk file for later processing by the Reformat
program. In addition, a small amount of reformatting is performed on certain
numeric fields.
2.0.1 Data Reformatting
Because of a change in keypunching conventions midway through the
project, reformatting of some of the data fields became necessary. The key-
punching conventions which were changed consisted of the following: Initially,
alphanumeric fields on coding forms were punched left justified in the data
fields of the cards, and numeric fields of the coding forms were right justi-
fied in the card data fields. Because this difference was time consuming for
the keypunch operators, the convention was changed so that all fields from all
coding forms were punched left justified in the card data fields.
The Edit and Reformat programs were initially written to expect right
justified numeric fields. Rather than changing the many places in the pro-
grams where reads were performed, the Edit program was modified to right
justify all numeric fields as the data cards were read. This function is
performed by subroutine RJUST. The details of this subroutine are described
later in this section.
2.0.2 Inputs and Outputs
Edit program inputs consist of (1) a single card identifying output
file names, and (2) keypunched data cards.
A single control card containing file names is used to define the three
disk files which are used during the processing of data. Columns 1-10 contain
the name of a disk file which is not used by the program. Columns 11-20 con-
tain the name of a disk file which is used to store intermediate results, and
is not needed after the program has finished executing. Columns 21-30 contain
the name of output disk files containing the edited card image records, in
which the numeric data fields have been right justified. This file is the
input file for the Reformat program.
Program outputs consist of the disk file referred to above, and a listing
containing (1) a list of all cards read and (2) an error report showing all
cards which contained one or more errors.
2.0.3 Processing
The Edit program processes all cards for a complete screen as a unit.
If no errors are detected anywhere in the screen, the cards are written to
the output disk file. If errors are detected, none of the cards for that
screen are written to the output disk file.. . *^
88
-------
A complete list of all cards read are printed, including the card's
position in the input deck. Additionally, when errors are detected, all
cards of the screen are listed and the card(s) in error are flagged.
The program performs a preliminary check on the cards in ascending
numeric order. If the cards are not in numeric ascending order, the set of
data cards is rejected and a message is printed along with the contents of
the set of data cards. The program also checks for missing data cards.
The program checks to see if the set of data cards belong to a valid
coding form. If the set is not a valid coding form, the set is rejected
and a message is printed along with the set of data cards.
In the coding form labeled Screen 1, the editor checks to see if the
sequence type (one of the data fields in the coding form) is a valid sequence
type (the thirteen different sequence types are labeled PR, AB, PF, ST, SG,
NT, FL, FG, TA, TG, LU, LG and RU, respectively). The coding form Screen 1 is
always the first screen in any sequence type. For every coding form, the pro-
gram checks for a valid screen label within the sequence type obtained in the
last Screen 1 read. If the screen label is not a valid one, the program
rejects the set and prints a message along with the contents of the coding
form. If the last Screen 1 read was rejected, the program will reject all
the subsequent screens until it encounters'a new Screen 1. The message
indicating the rejection of the previous Screen 1 is printed along with the
contents of each one of those subsequent screen types.
The program checks most of the data fields in every coding form accord-
ing to the sequences specified in the respective coding form or by some other
previously specified guidelines (outline of specific requirements).
If the-check fails, a message is printed along with the contents of the
coding form indicating an error in one of the data fields (located within
columns four to eighty). When the check is finished, the program reads a
new set of data cards and goes through the checking procedure once again.
2.1 Main Program: RESCREEN
The main program begins execution by opening the files to be used and
reading the first card image. The program prints both the card position and
contents of the data card image.
Because of the latest revisions to the TACB Emission Inventory Coding
Forms, the program calls the subroutine RJUST which in turn calls the
subroutine SHIFT. Both subroutines together right justify the numeric
fields of the data card images.
The program reads all cards of a screen and stores them in array IDATA.
It stores in JD the character in column one of the card image that identifies
the screen type. It also stores in the array NCOL the information obtained
in columns two and three of the card image that identifies the position of the
card image within the screen in the following way:
89
-------
NCOL (J) = J : The screen's Jth card image is valid.
NCOL (J) = -1 : The screen's Jth card image is not valid.
NCOL (J) = 0 : The screen's Jth card image is not present.
After all cards of a screen are stored in array IDATA, the program
attempts to identify the screen type. If the screen type is not a valid
one, the program prints error messages and processes the next screen. If
the screen is a valid type the program interprets the information on the
card images and calls the appropriate subroutines to test for validity. The
screen type is stored in variable KSCR. The valid values and their meanings
are:
1 = Screen 1 9 = Screen M
2 = Screen A 10 = Screen N
3 = Screen B 11 = Screen 0
4 = Screen G 12 = Screen R
5 = Screen F 13 = Screen S
6 = Screen J 14 = Screen X
7 = Screen K 15 = Screen Z
8 = Screen L 16 = Screen
After the screen testing is performed on the card images, the program
checks to see if the screen is valid:
IER = 0 : the screen is a valid screen.
IER = 1 : the screen is not a valid one.
If the test fails the program prints a message and begins processing the
next screen.
If the screen passes the test, the program checks for proper sequence
type and for proper screen type within the present sequence. The program
checks for proper sequence type when a screen 1 is present and also checks
for valid screen type within the sequence. If the sequence type or any screen
type within the sequence is not valid, the program prints a message and processes
the next screen.
The valid screens are stored on the disk file corresponding to channel
(or logical unit) ISCR2.
2.2 Screen Subroutines
The screen subroutines check almost every item present in each of the
card images. The testing is done to check for accuracy in filling in the
coding form and also to check for keypunch errors.
90
-------
2.2.1 Subroutine SCRN1
The subroutine SCRN1 checks the contents of the input data card with
the data requirements of Screen 1. The subroutine verifies that the year,
month, and day are within bounds. The account number codes and the sequence
type are also checked.
Subroutine input parameters:
J — number of input data images for Screen 1
IER — Error message
IER = 0 : No errors
IER = 1 : An error has occurred
NCOL — An array that contains the status of the input data card
images for the screen
JD — Contains the screen type (1 in this case)
IERROR — an array that contains the error status of the screen data
cards on return.
2.2.2 The Remaining Screen-Checking Subroutines
The remaining screen-checking subroutines consist of SCRNA, SCRNB,
SCRNC, SCRNF, SCRNJ, SCRNK, SCRNL, SCRNM, SCRNO, SCRNS, SCRNX, and SCRNZ.
These subroutines check the contents of the input data cards according
to the specifications given for the respective coding forms.
The parameters for these subroutines are the same as the parameters
for subroutine SCRN1 with the exception of the parameter JD which is not
included.
The processing of these routines is largely self evident from an inspec-
tion of the code. However, these special exceptions are noted:
The subroutine SCRNN checks the input data cards for Screen N. Since,
for multiple screens, the coding form for Screen N has specific requirements,
an added parameter for the subroutine is given by KOUNTN — The number of
screens of type N in the present sequence.
The subroutine SCRNR validates the input data for Screen R. The alter-
nate set in Screen R is passed to the subroutine as an added parameter:
IX — identifies the proper alternative
IX = Blank: Option one
IX = "X" : Option two
91
-------
2.3 UTILITY Subroutines
The following utility subroutines are used by the program to simplify the
data checking.
2.3.1 Subroutine ACCOUNT
The subroutine checks to see if the card numbers in card columns 2-3
are in ascending order. If the test fails the subroutine returns with an
error flag.
Subroutine parameters:
NCOL — This array contains the card number of the cards present on
entry. On entry, the elements of the array contain the following:
NCOL(K) = K : the screen's Kth card is present
NCOL(K) = 0 : the screen's Kth card is not present
IER — the error message is set to one if the test fails and is set to
zero if the test passes.
2.3.2 Subroutine OPENS
Input parameters:
I — If I = 1, the program opens the following channels (or logical
units):
ICARD — card reader
IPRINT — line printer
IDISK — file not used
ISCR1 — file for intermediate results
ISCR2 — output disk file
The file names are provided by the user. NAME 1 is a disk file which is
opened but is not used, NAME 2 is a disk file used during processing. NAME3
is the output disk file containing the validated screens.
If I - 2, the program closes the previously opened channels and prints
the messages shown below and then returns.
TACB-EI REFORMAT EDITOR
(NAME1) DISK FILE - NOT USED
(NAME2) DISK FILE - USED TO CHECK SCREENS
(NAME3) DISK FILE - CONTAINS CORRECT SCREEN SEQUENCES
TACB-EI REFORMAT EDITOR — END
2.3.3 Subroutine ACNUMCK
92
-------
Subroutine ACNUMCK checks the seven-character account number in the
following way:
(1) The first character (letter or number) is assigned a two digit
integer code number. If the character is a letter, the number corresponds
with the position of the letter in the alphabet. If the character is a one
digit number the code number is the character plus twenty-six. The left
digit is the first code number and the right digit is the second code
number.
(2) The second character is treated in the same way as the first
character. The left digit is the third code number and the right digit is
the fourth code number.
(3) The third through the sixth characters correspond to the fifth
through eighth code numbers.
(4) The seventh character is the check character. This character (code
number nine) is chosen to be the letter whose position in the alphabet (a two
digit number) satisfies the combination:
19* (code number one) + 17* (code number two)
+ 13* (code number three) + 11* (code number four)
+ 7* (code number five) + 5* (code number six)
+ 3* (code number seven) + 2* (code number eight)
+1* (code number nine) = 0 (modulus 23).
Subroutine parameters:
JD — This array contains the screen character account numbers to be
checked.
IER — Provides the error flag
IER = 0 : The check character of the given account number is valid.
IER = 1 : The check character of the given account number is not valid.
2.3.4 Subroutine CONVERT
The subroutine CONVERT is used to store the present screen in a disk
file for further testing. If the screen is valid, the subroutine stores
the screen in the output disk file.
Subroutine input parameters:
IDATA — This array contains the input data for the screen being processed.
J — number of cards for the present screen
L — L = 1 : Stores the present screen in a temporary disk file (ISCR1).
L = 2 : Stores the valid screen in the output disk file (ISCR2).
93
-------
2.3.5 Subroutine SEQUENCE
Subroutine SEQUENCE checks whether the current screen type is valid within
the present sequence.
Subroutine parameters:
IA — The array contains the sequence type:
IA(1): Left letter
IA(2): Right letter
IB — Letter corresponding to the screen type
IER — Error message
IER = 0 : Valid sequence and screen types
IER = 1 : Invalid sequence type and/or invalid screen type
2.3.6 Subroutine DEGF
The subroutine DEGF validates columns 21-25 of card F02.
Subroutine parameters:
LA — Array containing the string
IER — Error message
IER = 0 : All blanks or a letter (A or S) and up to four digits
IER = 1 : The first non-blank character not valid or the first
non-blank character is valid (A or S) but the remaining
characters are not all digits.
2.3.7 Subroutine ERROR
Subroutine ERROR prints a message when an error is found. The subroutine
prints the contents of the screen being processed and indicates the location
of the error within the screen (in most cases the program detects only the
first error, but in some cases can detect all the errors).
The message includes an eighty-column count to help the user find all
the errors.
The subroutine input parameters are:
IDATA — An array containing the screen being processed.
ICOUNT — Contains the location of the first card in the next screen
within the data card image file.
94
-------
J — The number of data cards in the present screen
IERROR — An error array which indicates with an asterisk that an
error has been found in the data cards within the present screen.
2.3.8 Subroutine RJUST
The subroutine RJUST right justifies numeric data fields on the
data cards.
Subroutine parameters:
IBUF — The array contains one complete card image.
2.3.9 Subroutine SHIFT
This subroutine shifts the data fields in the data card that need to
be right justified.
Subroutine parameters:
IBUF — This array contains one complete card image.
ISTART — This array contains the location of the data fields that
must be right justified in the card image.
2.3.10 Subroutine CHANGE
When Subroutine ACCOUNT detects an error in columns two and three of
the data cards, Subroutine CHANGE is used to set up the error message for
Subroutine ERROR.
Subroutine parameters:
NCOL — On input this array takes into account the missing screen's
cards. On output the array contains only the numbers (columns two and three)
of the data card images present for the screen.
IERROR — The array contains the error messages for all the data cards
in the screen on input and the present data card images in the screen on output.
J — The number of data cards present in the screen
95
-------
3.0 REFORMAT PROGRAM
The purpose of the Reformat program is to read the disk file produced
by the Edit program, reformat the data, and write the data to an output
disk file. The output disk file is in the proper format to be processed by
TACB programs.
3.1 Main Program; REFORMAT
The main program processes all input card images for a screen as a unit.
A set of cards which make up a complete screen are read by the program and
saved in array IDATA. Any missing cards for the screen are inserted into the
array and the appropriate subroutine is called to reformat the data and write
the data to the output disk file. Reformat counts the number of records,
screens, in sequences written to the outpjit file.
3.2 Screen Subroutines
There are 15 screen subroutines corresponding to the 15 screen types.
Each subroutine reformats the data in the proper way and writes 24 card
images to the output disk file.
3.3 UTILITY Subroutines
UTILITY subroutines are used throughout the program to carry out certain
common tasks:
3.3.3 OPENC
This subroutine opens all files.
3.3.2 REF
The subroutine REF is used by the subroutines REFJ, REFL, REFR, REFX
and REFZ to include in the respective screens certain information for these
screens which is available only in the first screen (SCREEN 1) of each
sequence type.
3.3.3 SCR
Subroutine SCR is used by all fifteen screen subroutines to create the
first line in every screen. Part of the information is available in the
first screen of each sequence. Other portions of this information must be
obtained from prior screens.
96
-------
APPENDIX G
SCC LIST
97
-------
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nr-rTOR =
XFACTOR =
XFACJQR =
XFACTOR =
XFACTOR -
XFACTOR =
XFACTOR =
XFACTOR =
XFACTOR =
XFACTOR =
XFACTC1R = X
SOLVENT
SOLVENT
SOLVEN T
SOLVENT
.1(11 VFNT
SOLVENT
SOLVENT
SOLVENT
SnLlfFNT
SOLVENT
SOLVENT
SOLVENT
SOLVENT
SOLVENT
SOLVENT
TANK CARS/TRUCKS SU6ME'RGEO LOADING
CLEANED CARGO TANK
NORMAL DEDICATED SERVICE
DEDICATED VAPOrt BALANCE
IANK r ARS/TRUCKS SPI ASH 1
CLliANCD CARGO TANK
NOHHAL DEDICATED SERVICE
|)Fl)ICATfG VAPOR BALANCE
VEH LOAD STATION liNDEKGRO
SPLASH LUAOING
SUd LOAD-UNCONT
SUd LOAD-OPN SYS
sin LiiAn-r.LS SYS .
UNLOADING
SPECIFY MFIHDQ •
ft*. *.ft*ftftft*ftftft.ft ft ft.».*.ft.«__ ft*ft* ****
VtH LOAD STATION FILL VEH
VAP OliP LOSS
LIO SP ILL LOiS
OTHErt LOSS •
SH |P S SUtMEPGr
CLtANEO CAPGO T»NK
NORMAL DEDICATED SERVICE
..BALLASTED 1 ........ ...
10^0 GALLONS PUMPED
i3jo GALLONS PULPED
l?i)0 GALLONS PUMPED
n AD INT.
1000 GALLONS PULPED
10CO GALLONS PUMPED
1OO-) GALLONS PUMPfO
GASO STG
ICOO GALLONS, THANSFERREO
l^iiJ GALLONS IBiNSFEhHEO
I;)0« GALLONS TRANSFERRED
100^ GALLONS TRANSFFHRKQ
1000 GALLONS TRAMSfEhREO
IJDQ GALLONS TKANSfERfiEQ
********* .,
GAS TANK
X
l^DT GALLONS PUMPED
100^ GALLONS PUHPEO
10?1? GALLONS PUMPED
0 LOADING
i )tn. .GALLONS PUMHEU..
I-'".'! GALLONS PUMPFU
I!'' 1..GALLCNS PUHPEU..- _
VAPOR PRCSS
VAPOR PRESS
VAPOR PRESS
J4POR—PHESS
VAPOR PRCSS
VAPOR PRESS
-- VAPOR. RRESS
VAPOS PhESS
- VAPOR. PKESS
HOL HEIGHT
1 MOL HEIGHT
MOL HEIGHT
MOL HEIGHT
MOL HEIGHT
HOL HFIGHT
J
_
HOL HEIGHT
MOL HEIGHT
. MOL HEIGHT . ... . .
-------
oo
POINT SC EVAP
4-10-0.) 1-99
POINT SC EVAP
4-ll-OOl-AA
4-H-Olil-AC
4-1 i-oo i* AD
****************
POINT SC EVAP
4-12-OiM-AA
4-17-OQ1-AB
4-1Z-001-AC
4-12-OG1-AD
POINT SC EVAP
4-lZ-OOa-99
.P.QIHI...SC FVAP
SHIP; BALLASTING LOSSES
GENERAL/NflT CLAS-S1FIEH pmo r.AIIHMS RAIlASTm
i* *••*••••»••••»•*• •»•••«»•«•»••••*•
OCEAN UAKGES SUBMERGED LOADING
CLEANED CARGO TANK 1000 GALLONS PUMPED
UALLASTEO 1051 GALLONS PUMPED
AVERAGE TANK CONDITION -• • l^OO GALLONS PUMPED
BARGES SUBMERGED LOADING
CLEANED CARGO TANK IOCO GALLONS PUMPED
NOftHAL nff)|r»Trn SFRVICF \nr.n r.&i | HMS PIIMPFD
BALLASTED 1000 GALLONS PUMPED
AVERAGE IANK CQNU1TIGN flO) GALIONS PIIMPFO
BARGES TRANSIT LOSSES
GENERAL/NOT CLASS1FIIO HEEK-IOOC GALLONS
HI sr HC FtfiP -siiPHKRr.rp in»niwr.
'VAPOR PhESS
VAPOR PRESS
VAPOR PHE SS
, VAPOR PRESS
VAPOR PRESS
VAPOR PRESS
VAPOR PRESS
VAPOR PRESS
HOL HEIGHT
HOL HE ICH T
HOL HEIGHT
HOL HE IGH T
HOL HEIGHT
HOL HEIGHT
HOL WEIGH?
DENSITY
A=.9 0-0 01 = A B NORMAL- aE 0J CAJ£_D_i£H V-l.C E
iaca_fiALLOMS_P-UMP-EO
_VAP-OB_PHE-SS
-HOL-HEICl
•*,*-**_*.*.*_*.** * *.* 1L*.* * * * • • * ** * * » **
POINT SC EVAP MISC HC EVAP
*.*.*-• •***»»*****»•
SPLASH LOADING
*-90-0^-A8 NORMAL OE01CATED SERVICE
1001 GALLONS PUMPED
VAPOR PRESS
HOL HEIGHT
- P 0 INI ..SC -. EV Afc
. __ A-90-999-99
MI SC-HC- EVA^E
-CI-HES/MOI-.CL-AS1F.O
SPfClFY I HI REMARK
_».•«•**»»•«•»«».«••._»• «»*.**». *.t .*.*.«_*_*.*.* •» «.*.•.**««..».»_*_« •**.*_
SOLID MASTt GOVERNMENT MUNICIPAL 1NCIN
5-Cl-Oul-Ol
MULTIPLE CHArtBtR
_SiN'3iE CHAMBER
TONS BURNED
TONS 3USNEQ
SOLID HASTE
s-cr-ooz-o'T
GOVERNMENT
CPEN BURNING DU1P
GENEHAL
LANQSCAPE/HHUNI NO
-u 1-002-Ci JET FUtL
IONS 9URNEU
TONS •1URNED
•HUNOHE05 OF GALLONS
_SOL10 WASTE Gf)VL.HK.tO.L-
.INClNEHATOh
5z
-------
SOLID h.ASTt.. .._ .....
5-C1-900-.0. _____ rtESlOllAL Oil......
5-01-900-05 DISTILLATE OIL
ATURAL (i«S
=. Q.6
_ . •lO'J.'i...GA_LLON.
• 1HO? GALLONS
'MILL1HN CUBIC FEET
f i
5-C 1-9CC-10 LPG
.5-3 l-9QCr9r OT;.Ert/NCT__CLASi£D
5-01-9(,i;-98 OTHER/NOT CLAS1FO
• I..} GALLONS
_.*HILJLlON..CUBIC-r££J_.
•101;- GALLONS
_. • .1.0 N.S .
SOLID HASTE
COMH- INST
INIINEHATQH GEN
5-02-001-01 MULTIPLE CHAMBER TONS .URNEO
5.i2-00 1 ?.C2 _SI.NGLE._CHMB£.R T.ON.S_8URNEQ
5-OZ-OOl-OJ CaNIHOLLLO AIR TONS BORNEO
5-u.2r04li£Ji cnmcAi. -hFFUsr rnfjs niiRMFn
5-OZ-0'Jl-«i5 CONICAL-HOOD TONS 8URNEO
SOLID -WASTE tOHMTUNil OREM-BURNING —
5-QZ-Q j g-q l HOOP TONS rtMHNrQ
5-'j2-OOZ-Ci REFUSE «TONS 3URNEU
SOLID- MASTE- . ___CU.MK=.IN5I tPiRIMFMT 1NCIN
•j-Q?-!)f. j-0 1 ft UC FED- Tims JtllRMfD
5-'jZ-Oj3-Cd FLUE FED-MODIFIED TONS BURNED
_____ :
- - —
**•*>*•»•••****•* .•••.»»••«•>«••• •*>..*>.»••«•*>.
SOLID... HAS.T.E.__ CQ.MM^.IN.S.1 IJȣ.I.NER*.T.Oh___
. 5-32-01.5-05 PHTHllL nGl C*L .(INS BURNED
5-i/a-C..5-06 SLUOGE TONS DRV SLUDGE
*iOMS_dUH.HEa
^ J»A t-i-»_*.lL*.«
SOLID MASTE COHH-1NST AUX.FUEL/MO EHSNS
i )
5-02-900-0«. RESIDUAL OIL
5-.Z-9CC-=CS 01 STILL ATE.-OIL
,b NATURAL GAS
1C LRG
GALLONS
•MILLION CUBIC FEET
—• 1343_GALLOWS
OTHE.J^i GALLONS
• TONS
•***••*•••*
-SOLIU WASTE
INaUSThlAL-
_£-
JNCINEhATOR.
J.QU s aus.it£o_
5-G3-QOI-02 SINGLE
_5-J3rOv;.l.-03 -_ CONTROLLEO-A1R_
5-0 3-Oxil-0-C 1 .. HOOD ...
TONS '1UF. HEi)
-------
5-33-OU3-03
5-o3-ooz-ot
AUTO 8 OOV-- CONPT S
COAL REFUSE PILES
TONS-flUBNEO --------------
CUBIC YARDS or PILE
_S J1L1D— H tSXE
I MlillSTM Al
AUTO HOdY INCINftJ-
-5'J J.-OC-J«01
5-03-^03-Oi
H/0 AF-IEhflUHNEK
H/ AFTERBURNER
AUTO S
AUTOS BUKNEO
LllL_h VSJ£
BAII CAR
UEE.N
*C-AR.S_a.UBNEO __ . _________
SOLID WASTE
INDUSTRIAL
INCINERATOR
5-03-005-06 SLUDGE
_5=43--005.-.3.9 ________ O.TH£LM/MOL-C1.4SLF-D
TONS DRV SLUDGE
X SULFUR
SOLID MASTE
INDUSTRIAL
»U>.FU£L/NO EHSNS
5-03-9UO-J*
J5-U J-900-C5
5-0 3-900-06
5-Q 3-9uO-07
5-03-900-10
. 5-03-900-98
5-G 3-900-09
SESIUUAL OIL
OisT ILL ATF HTI
NATURAL GAS
PROCESS GAS
L P G
OTHER/NOT CLASIFD
OTHEH/NOT CLASIFO
OTHER/NET CLASIFD
1090 GALLONS
irt)1) MI I ONS
MILLION CUBIC FEET
MILLION CUBIC FEET
1003 GALLONS
•MILLION CUBIC FEET
•IOC) GALLONS
* TON S
X SULFUR
X SULFUR
X SULFUR
X SULFUR
X SULFUR
t •_».« »_t*_*^ *.* •_••.*.•-• «>««««««««««««»«« « « 4 «
LIOU10 HASTE 1NUUSTHIAL INCINERATOR
6-01-001-01
6rJ3r001-OZ
6-J3-3J1-03
HULTIPLE CHAMBER
SINGLE_CKAM3ER_
CONTftQLLCO AIR
TONS BURNED
IQNi._a.UBJlEO
TONS 8U«NEO
-JLLS.CE.LL.AN.E.DJ1.S FEDRL NQNEH1TTERS CTHFK/NQT CLASIFD
9-J1-999-99 SPECIFY IN BEMASK
*.I.MS.LA.lLATJUIiS.(EAC.Hl_
*AREA/ACR£S
!LE.hl.CL£_
----- 9-OZ-Oul?AA ---- hOAO- OUST
VEHICLE Hi LES -TRAY t LEO ___________ XFACTOH- J.-
-------
APPENDIX H
POLLUTANT CODE LIST
151
-------
EI18/POLLUTANT/OA1A/NUM
Mud L*I• H*nt.n
G.
KJ'
100
360
4CO
500
610
801
1000
1210
1*00
1600
I 7(0
laco
2000
2200
2400
2600
fTOO
2 (HI
31CQ
HOI
34CO
3500
3600
3/00
3800
4100
4200
(, j<;(5
4600
4600
- — 4900
50CO
•J1C4
5 500
55CO
5600
5800
5900
6000
00000 NO PCLLUTANT
0100C TOTAL PARIICULAIE
G14J1 TOTAL LEAD CMPNDS
' C5COO TUTAL REACTIVE HC
07c4(t TOTAL NOX
C7C51 TOTAL SOX
ic coo PART - u
lltOU PART - CHEMICAL - U
HIT AMMq^IUM CDMPmiMn - II
111C5 AMMONIUM CHLOMOE.NH4CL
1U10 AMMONIUM NITRATE, NH4Ni 3
11115 AMMONIUM SULFAT(NH4 )>SC4
11155 CHROMIC ACIO
11160 HYOKCCHLORIC ACIO
11164 HYORIOTIC ACID
11165 NITRIC ACID
11166 HYDROCYANIC ACID
1117C PHOSPOR1C ACIO
111/5 SULFUHIC ACIO
11200 CONOENSO ORGANICS-U
11210 FORMALIN
1J2»5 CYANIDES (SOLID) - U
11230 FLUORIDES (iXCEPT HF )
H"5 lOOIOtS tEXCEPT Hll
Il24u PIGMENTS - U
H^SO PLAiTirS - U
11255 POLYETHLENE
ii26<:. pin tpfcfiPYi FNF
11265 POLY VI1NYLCHLORIDE
ll^fi- pFsrir.iftF PARI - n
11300 INSECTICIDES - U
11430 INSECTICIDE PAHT-U
116CO HERBICIDE PART-U
ll'jOO FUNGICIDE PARI-U
l2CGu PART - ANIMAL - U
12 100 31 00n
1210C OAlfiY PRODUCTS
125ri<> MILK
12115 CHEESE
124CO FATS ANMAL
12/.U' MEAL ANIMAL
12720 ^LOOO Mt'L
12730 JUNE M£AL
\7 1 1^ FISH ME AL
12760 POULTRY MEAL
126CC MEAT SMUKINCi
13CCC PAST - VEGTBL—r U
13010 ALFALFA
13!v40 CtLLULGSc
13i*5 SAWUUST
13C60 CUFFF.t
13C/0 COMPOSTED M^TLRIAL
IJL-et; COTTON
^^B . ^^H
._O..PO.O.
O.)00
o .ao^
0 .00?
n » i o^
0 . -"^ rt A
i) .joO
? .DOT
O.O'JI
*"oil
C .000
0 .00^
0.101
o.oo^
"> .OCn
o.coo
P,000
5.001
•? .000
0.0'J3
9.000
O.OC1
3 .003
- 3.«J
0 .3 30
n . o .) ">
0—0 CO
r, ,0i)0
•>.ooo
3.^,>0
o.;oo
o.oo '>
•: .00-)
j .000
1 .•>•.)•:
j .'JO'-
HI
O.C
O.C
0.0
0.0
n.c
0.0
0.0
0.0
Ti.O
0.0
0.0
O.C
0..0
O-O
0.0
0.0
0.0
5 .0
f).0
3 jO
0.0
5.0
O.C
0.0
0.0
n .0
O.C
o.o
0.0
0-0
0.0
1,0-
3.0
n .0
0.0
O. !)
0.0
0 .0
3.0
|> t 0
O.C
Cj 15
O.C
" 0
0.0
0.-1
0.0
•> .0
0.0
) ^*
1.C
J."
1.0
•;. c-
0.0
•-' 9 "
^^B H
1 .C
O.C TOTAL PART
O.P TOTAL LEAD
0.0 TOTAL REACT HC
0.0
0.0
O.f! PART-CHEH-U
o.f AMMON rupn-ll
O.G NH4CL
0.0 NH4Nni
1.C
0.0 I CMPDfFXC HI)
n'o
0.0
O.C PVC
f)-fl PfSTICIOC P»-U
0.0 INSECTIC10E-U
n.o INSCTICID PA-U
0.0 HERBICIDE PA-U
f>,r FIJNGTCIDF PA-lf
0.0 PART-ANIHAL-U
0 .C
0.0
o.o
?.o
O.r,
o.o . . ( .
c.n PART-»FGTBL-U
0 1°
1.0 '
f> .i1
0.-'
n , r CIMPO.ST Miri ... . . ..
1.P .
1 f
-------
tn
6*01
66CO
f,7l)0
68CO
b 9ljO
7001
7100
7203
7300
74C3
7503
76C1
tree
78oo
7900
aoco
81C1
621/0
8500 •
0*00
HSdft
d600
aroo
6800
6 9C 0
90 CO
4l6n
92C9
* ?<>')
9400
9Si;0
96tO
9700
98C1
99CO
lOOuG
10100
iu2to
1C JOO
10400
10 SCO
10600
10700
10 eon
109CO
110CO
11 ICO
112CO
113CO-
114CO
115'iO
11600
11 7CO
lien
119CO
120CO
12 ICC!
122u-5
12300
124C1
125CS
ii**Oi' niTTriu^rrn
13L9£ HULLS
ii£ oil riiTTn*j<;FFCiiMT
13096 MEAL VEGETAUL
13130 FEED MIXTURES
l?14r- FLO^JR
13144 H1CE
11 146 WHF A I
13150 FOOD PRODUCTS (GEKEML)
13)6(1 GfUIN
13162 CHAFF
l * I f,t sf rn cnA TS
13170 GK4SS SEED
}3 JBg HAY
1319U LEGUMES - U
13200 PEANUTS - U
13205 PEANUT MEAL
13210 PEANUT OIL
13215 PEANUT PLT M TLC HULL »E TC )
13»?u SOYBEAN
13225 SOYBEAN MtAL
HP?') soYflFAN nil'
13235 SOYUEAN PLT MTLtHLS.ETC)
13250 SPICES
13260 SUGAR
1 1 > 7 r. 3
14C16 ALUM1NH OXIDE- ALZ03
14C16 4AUXI1E
14C2u 4NII10HY-SJ
14C22 ANTIMONY TETRAHtOKlTE
140?Q ARSENIC - AS
14032 ARSENIC TRIOXIOE -AS?03
14l)J;i 4RSINE.4SH3
14C35A AnSENIC HYDHIOC.ASH3
14C4G ASBESTOS
14C50 1AHIUM - 8A
14C52 RARITE - HAS04
14C54 dARlUM CARaONATE-eAC1 3
I4(j5b BARIUM CYANIDE-HAtrnl?
I4t56 BARIUM HYCftUX 10£-HAIOH)^
I4'j59 BARIUM SILJCIUL
14C6C -aENTOMIE
!4C7w atHYLLlU^-Ut-
l*tec HlS1UTH-dI
HijQl;- iJURO^-q
14UC CADMIUM-CO
14H2 CAQMIU1 OXIU£-COO
141H CAOHIUH NITHATE-CC(NO 3)2
14l2ii CALCIUM
14122 CALCIUM ALU1NAT SILICATE
14i'i Oftl C lUM_CAPnaNATr-CAnu?
14124 CALCIUM F LUO R 1 D£ - C A f »
.14126 CALCIUM QX1UE-CAQ
14H6 CALCUM SULFA T-C AS j«-.'H2^
1414. CA»80N-C_ „ . .
0 * C"
0.00"
i n§^ i
0 .0(30
P P fi 0
0.001
r .oijr
0 .00')
n .n-i".
O.')00
". .?<-,.•>
o .oor •
C ,^0r
O.JOO
ft .005
O.OOT
1 -0
0.001
1 iOOO
O.OC1
O.TOO
0 ,001
0 .101
0 .10^
0 .000
•> .101
0.100
0 .000
1 .our
o.oo-i
o.ion
0 .001
1.000
1.0 JO
0 .001
"'-TO'1
O.TJJ
f . 0 il r'
? .DOO
fl.1^1
j .00?
o. .rsc j
0.100
- - - Q . 3 i j )
1 .OCrl
0 ]'•••'•
7 . i 0 )
C ,nJO
1 .001
r .3 TT
*. '•?«•>
. - - -• . 0 j •""
i .•':•'•:
•;.-•!.•;•'•...
C P
0.1
0 0
0.0
1 p
1.0
a-,0-
C.1
o.o
0.0
1-0
0.1
>; T il
3.0
c.o
3.0
P.O
0.0
0.0
5.0
U. 3-
•5.0
r.n
0.0
3 il
0.0
r> n
0.1
* . 0
0.0
C .0
c.o
£..-•"•
0.0
0.0
0.0
o.c
I}.?
Q.n
1.0
P.O
n.i
3.0_
"••.o
0 .1
c.o
0.0
1.0
n.&
1.0
1.0
-.0
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0.0
1 .0
•!.^i
0.3
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i«"
'.' . '.'
n .<•
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" . '' .
0 C
0.0
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c.o
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a.r
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0.0
0 , r .
1.0 FCCO PROO(GEhL)
OTO
3 .n
n .0
0.0
0-n
0.0
o.r
0.0
0.0
1.0 PEANUT PLT MTL
n.f,
o.o .
O.o
1.0 SOYBEAN PLT HTL
0 0
o.c
0 0
0.0 SUGAR (8GASSE)
1 .0
0.0
1.0'
o.c
O.C ALCLJ
0.0 AL(OH)3
3.0 AL7Q3
0.0
0.0
O.P S8 TcTRAHEORITE
1.C
Q.O AS203
O.C ARSINE.ASH3
0.0 AFSINE.ASHJ
1.0
0.0
1.0
O.C 8ACU5
n.o HiirNl/'
1.0 8A(OH)2
•> . o
1.0
O.C
1.0
O.o
O.C . . '
i) .r COO
3.0 CD(N03>Z
." . 0
O.r CA ALUM SIL1CAT ,
.1-0 CAC05
1.0 CAF2
ft . r- C A n
•J." CASQ4-?H?0
.0.0 . . . ..
-------
12/tu
12800
.12900
13000
141*4 ..COM --------------
1<>146 CUKt
1415L .CESlUMrCS _______________
I416t. CHROM1UH-CR
14ife.? r.HRnHiiiM nxinr-rsn
.coo—.
.001
-3...0 Q
0.1 0
..9 .0 0
0 . f- 0
n.n n
Q
0 ,
o
0
n run
13200
13300
134CO
13500
13600
U/-CO-
13BGO
-: 1.J9GO.
140CO
14.1CO-
14200
14JCQ
14400
J45UO.
14603
14/CO
14600
UL9liO_
14200
142 1C
l4^^^
CORALT-CO
...CUPPEh-CU
oiMOMi re
-F.£UOjHAR
CrtYUL ITE
GEHMANIUH-G-:
.uULQ.-AU
1*2*0
1*290
l*-3.Q_l,
14302
. 1*3.0 *
1*306
.. 14306
14310
IRIOIUM-IR
-LB 9 Hr£E
IHON i CHLOHIOE - F£CL2
-I RON_i_CliLafi.LOL_=_.F.t£L.3-
IrtON 2 OXIDE - TEC
lftQN._3_QXlD£._-._FE-213
LEAO-P8
LEAD OXIQ£ - U
.001
.-.O-ti.
.000
_-i...a a.
i.o o.
_o.o a,
0.0 0.
3 .C Q.
f FECL?
.C...E£.CLl.
0 FEO
K
15000
151CQ_
15200
13300...
154CO
UJ5C
15600
_ 15/CC-
158CO
.-1S9CQ
16000
1*316 LCAO? OXIDE
-1*316 .L£ADA_Q1U.EE ______
1*325 LITHIUM-LI
—.14335.— .MAGNESlUM-Mii _
1*342 MAiiNESIUH CHLOR 1DE-MGCL2
nirinF-Mr.n _
1435C HANGJNESE-MN
—14-J54 MANUANESE_01.QXlOE.-MlkO^
1*360 MtRCUKV-HG
143/C MICA
-1*4 VJ 14-3 8ii *OU *~8 OENUM-40
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.43
b'J
6?
G
A
*4
.a.
0
_jj
0
•
•
•
•
. •
•
I..
1
1
0
0
r
<•
0
CH3 HEKCAPTAN .._.... .'....
CAHBONYL SULFIP
DIMETHYL SULFIO
PF.SIC10 ORG-U
INSCTCO ORG-U
HER8CIO flRG-U
FUKGC1D ORG-U
) 59uC3 GASOLINE
) ^9004 JF T FIIFI
1 59C15 KEROSENE
1 b'1* lij " K»l t Tf
1 59 C 5i SCU FEED
S9C7G Col*-" fffo
! 59C'>y CUNOENSATE
1 59150 (HESfL
1 59175 FCC FLED
) 59 701CO HALOGEN-U
>.. 701C5...JROaIN£ . ... ._
) 7CUC CHLORINE
> 70 U4 CHLDS1NE TRIFLUURIOE
I 70112 CHLOhlNE DIOXIDE
) 7C115 FLUORINE
) 701Zi IODINE
! /O 17C ACIO GAS - U
1 70173 HTOHOOFN UNOHIOE. HER
i 70200 HrOhCGEN CHLORIDE
) ?025'j HYOHCGEN FLUORIDE
) 70275 HYDROGEN IODIDE
) . 7030L' HYDfcCGEN SULF IDE .. .
) 70 35-: METAL WAPOR-U
1 70 ^f,^. Mf Rf.UKY VAP'lti
/ 7C3HO OSr.ANO-METALLIC VAPJO.-U
1 - 7C3H5 NICKEL CAfidONYL - Kl(CO)4
1 704T.J II1THOGEN OXIDES
1 705Co SULFlih OXlDirU _
0.000
0 mn. *"
!).00')
0.00?
S:SS'
0 .000
0.000
0.000
0.000
0 .JOT
0 .000
o.ooo
0-000
0 .000
0 « 0 0 0
0 .000.
0 rllOO
0.000
o -"00
0.001
olooo
0 .000
LOCO
0 . " 0 ?.
0 .000
_D .OJ) )
0 .001
r- _oo;>
0 .00)
0 .00-1
0 .*0n
. 0 ,'i")
r .)l)'l
o T'>';:<
° .•:••.•>
0 .JO'
1 .r-i;'".
<> .31-1
' o.o o.o
fl,l* 0 , 0
0.00.0
o.o o.o
0.00.0
} . n r> , i
0.0 0.0
5.0 O.C
o.n o.o
c.o o.r
0.0 0.0
3 .3 a .n
n.o o.o
0 . 0 C.O
o.o o.o
3.0 0.0
0 .P O.o
i.o T.O PRCC^S ruet «;AS
0 . C 0 . 0
n.o i . .•)
0.0 0.0
n. n i- n
0.0 0.0
0.0 0.0
91Q.O 1 £ • f
l.C 0.0 INORG GAS-U
I^Q -f 17.O -
C . C 0.0
n . o >1 . c
0.0 1.C
0.0 159.6
0.0 71.9
r>.0 0-0 CHLTMIN TRIFIf-n
3.0 ' 0.0 CHLORINE 010X10
0.0 38.0
0.0 25J.8
- 774.0 '.f.
1.0 C.O
0.0 81.0 HHR
0.0 36.5 HCL
0.0 •>}." HF
•j . 0 148.0 HI
568.0 34.1 HZS
i . c o . c ,
r.i- »n . f.
0.2 -O.R OftGANO-KETL VAP
O.o 0." NICKEL C»S80N¥L
0 . :•• 4 & . 0
'' . r> <: . ''
-------
51'JOJ
5 1 1 0 0
5 1 ZOO
51 300
51*00
51603
51 TOO
51810
51900
7C5U; SULFlih DIOXIDE
7f-51i SULFUR IfilQJtlUE
71GOJ PESTICIDE INOhG GAS-U
711CQ INSECIICIDE INDfiG GJS-U
/liai PHOSPHINE-PHS
7lJCu FUNGICIDE INOftG GAS-U
'l^tC HYDRA2INE
arcCw o/oNt
91 inn nuuriti ninvinr
5£CUQ 90301 CARBON MONOXIDE
5>1f;.1 99999 nnilH-ll
0 .001
o .001
1 .001
t .OX.1'.)
0 -OC11
DIN •% l\
• J VI
a .o"i
0.000
i *"^
i'i_
'•.0
2.0
0.*
0. -1
0.0
b<.. i sue >
-H5.-1 SO?
1.0 PESTCIO INQRG-U
;).3
3.0 HFFpr in ?MnRr,-u
0.0 FUNGC1D IMORG-U
1 - ')
ft.fi *8.r
O.D &4.n
" .0
... o.«
c H • •"•
n.r . •
-------
APPENDIX I
QUESTIONNAIRE
ACTIVITY SUMMARY
161
-------
CTi
N)
1.
2.
3.
4.
5.
6.
7.
8.
9.
10.
11.
12.
13.
14.
15.
16.
17.
18.
19.
20.
21.
22.
23.
24.
25.
26.
27.
28.
29.
30.
31.
32.
33.
34.
35.
36.
37.
38.
39.
40.
41.
42.
43.
44.
Account
Number
HG-0235-K
HG-0233-0
I1G-0391-S
HG-0434-C
1IG-0231-S
HG-0019-S
HG-0033-B
IIG-0035-U
HG-0036-S
HG-0175-D
HG-0310-V
IIG-0048-L
HG-0225-N
HG-0562-P
HG-0713-S
HG-0218-K
HG-0674-D
HG-0543-T
11G-0696-Q
HG-0240-R
HG-0129-K
IIG-0028-R
IIG-0045-R
HG-0071-Q
IIG-0758-T
HG-0566-1I
1IG-0300-B
HG-0230-U
IIG-0234-M
HG-0157-F
HG-0114-A
I1G-0582-J
I1G-0326-G
HG-0356-U
HG-0294-R
IIG-0712-U
1IG-0191-F
HG-0537-0
HG-0672-il
HG-0039-M
HG-0558-G
HG-0017-W
HG-0770-G
HG-0194-W
Action: 1
2
Name
Confidential
Total Total
Ungrouped Grouped
Points Points
Exxon, S. Houston Terminal 3 1
Exxon, N. Houston Terminal 4 1
Ideal Basic Industries 25 9
LaGloria Oil & Gas 3 1
Exxon, Baytown Terminal 4 1
American Can Co. 172 7
ARCO Chemical Co. Yes 8 8
ARCO Polymers, Houston 19 10
ARCO Polymers, Deer Park 4 3
Crown Central 46 40
Gulf Oil Chemicals 129 34
Atlantic Richfield,
Houston Refinery 121 101
Ethyl Corp. Yes (30) (20)
Petro-Tex Chemical Yes 53 (36)
Tenneco Chemicals Yes 65 ' 65
DuPont Yes (44) (36)
Southland Paper 11 11
Paktank Gulf Coast 6 6
Stauffer Chemical.
Baytown 3 3
Fertitex (Stauffer Chem.,
Phosphate Chem.) 9 9
Champion Papers 36 29
Anchor Hocking Corp. ' 44
Ashland Chemical , 17 6
Big 3 Industries 10 10
Union Carbide, Linde Div. 11 11
Phillips Petroleum 25 16
Gulf Coast Portland
Cement 18 17
Exxon, Tomball Gas Plant 8 6
Exxon, Clear Lake Gas
Plant ' 8 8
Coastal States 16 8
, Cameron Iron Works 21 18
Port of Houston Authority 1 1
HNG Petrochemicals 11 6
Houston Lighting & Power, ••
Deepwater Pit. 4 3
Griffolyn Co. 42
Tenn-Tex Alloy 7 7
Diamond Paint Co. 22-
Oxirane Chemical Yes (6) (6)
Southern Pacific Transp. Co. 4 4
Armco Steel 67 65
Pennwalt Corp. Yes 18 (18)
Amerada Hess 18 5
U.S. Industrial Chemicals Yes 36 28
Diamond Shamrock,
Battleground Plant 6 6
• Coded and keypunched by Radian, delivered on magnetic tape.
: Partially coded by Radian, to be completed and keypunched by TACB.
Points
Not
Coded
1
0
12
1
1
34
( )
3
107
10
24
3
60
7
16
35
0
9
11
1
26
6
5
4
0
12
0
1
7
2
13
1
2
0
2
3
5
(10)
11
32
( )
3
11
10
Telephone
Contact
Yes
Yes
Yes
Yes
Yes
Yes
Action
1
1
1
1
1
1
2
1
1
1
1
1
2
2
1
2
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
2
1
1
2
1
1
-------
UJ
45.
46.
47.
48.
49.
50.
51.
52.
53.
54.
55.
56.
57.
58.
59.
60.
61.
62.
63.
64.
65.
66.
67.
68.
69.
70.
71.
72.
73.
74.
75.
76.
77.
78.
79.
80.
81.
Account
Number
GB-0055-R
HG-0192-D
CB-0004-L
GB-0001-R
HG-0665-E
HG-U659-W
HG-0656-F
BL-0051-F
HG-0632-T
BL-0042-G
BL-0034-F
BL-0005-M
BL-0026-E
BL-0043-E
HG-0126-Q
GB-0076-J
HG-0289-K
MG-0412-M
HG-0355-W
HG-0353-D
HG-0262-H
IIG-0229-F
HG-0232-Q
GB-0077-H
HG-0130-C
GB-0028-U
BL-0038-U
HG-0357-S
HG-0769-0
GB-0060-B
HG-0358-Q
GB-0037-T
HG-0714-Q
HG-0261-J
GB-0031-I
HG-0664-C
IIG-0392-Q
Action: 1
2
Name
Confidential
Marathon Oil. Texas City
Diamond Shamrock, Deer
Park i
Amoco Oil, Texas City Yes
Amoco Chemicals, Texas
City Yes
Solcex Polymer Corp. Yes
Shell Oil
Shell Chemical
Shlntech Yes
Rohm & Haas
Phillips Petroleum,
Sweeny Refinery Yes
Houston Natural Gas
Propane Co.
Amoco Production Company
Exxon, Pledger Gas Plant
Phillips, Brazoria Gas Plant
Celanese Chemical, Bayport Yes
Union Carbide Yes
Goodyear Tire & Rubber Yes
J. M. Huber
Houston Lighting & Power,
Webster Pit.
Houston Lighting & Power,
Greens Bayou Pit.
GATX, Galena Park
Exxon Chemical, Baytown
Exxon, Baytown Refinery Yes
Union Carbide, Marine •'
Terminal
Charter International Oil
GAP Corporation Yes
Monsanto, Alvin Yes
Houston Lighting & Power,
Wharton Pit.
Upjohn
Monsanto, Texas City Yes
Houston Lighting & Power,
Sam Bertron Pit.
Houston Lighting & Power,
Robinson Pit.
Tenneco, La Porte
Fractionating Pit.
GATX, Pasadena
Gulf Chem. & Metallurgical,
Texas City Yes
Smith Industries
IMCO Services
Coded and keypunched by Radian, delivered on magnetic tape.
Partially coded by Radian, to be completed and keypunched by TACB.
Total
Ungrouped
Points
38
42
121
(24)
(13)
120
147
16
128
98
5
36
7
18
21
254
99
43
6
9
6
70
7
10
77
6
79
26
19
63
10
8
9
5
8
19
13
Total
Grouped
Points
35
37
(119)
(22)
(13)
83
123
11
60
(54)
5
36
7
14
20
(93)
(30)
17
3
5
6
33
(7)
10
58
(6)
78
24
13
56
5
4
9
4
4
4
12
Points
Not
Coded
3
65
12
( )
(9)
15
42
4
35
9
3
10
4
0
(16)'
65
(73)
8
2
0
12
5
( )
8
9
(5)
26
1
33
21
0 .
1
5
5
5
18
2
Telephone
Contact
Yes
Yes
Yes
Yes
Yes
Yes
Yes
Yes
Yes
Yes
Action
-------
Total Total Points
Account Ungrouped Grouped Not Telephone
Number Name Confidential Points Points Coded Contact Action
82. BL-0004-0 Amoco Production Co.,
Alvin 27 23 1 1
83. BL-0029-V Gulf Chem. & Metallurgical.
Freeport 752 1
Action: 1 = Coded and keypunched by Radian, delivered on magnetic tape.
2 = Partially coded by Radian, to be completed and keypunched by TACB.
-------
TECHNICAL REPORT DATA
(Please read Instructions on the reverse before completing)
1. REPORT NO.
EPA 906/9-79-007
2.
3. RECIPIENT'S ACCESSION NO.
4. TITLE AND SUBTITLE
Evaluation and Processing of Houston Area Emissions
Inventory Data
5. REPORT DATE
March 31. 1979
6. PERFORMING ORGANIZATION CODE
7. AUTHOR(S)
D. B. Cabe, K. K. DeBower and M. A. Magee
8. PERFORMING ORGANIZATION REPORT NO.
9. PERFORMING ORGANIZATION NAME AND ADDRESS
Radian Corporation
8500 Shoal Creek Boulevard
Austin, Texas 78766
10. PROGRAM ELEMENT NO.
11. CONTRACT/GRANT NO.
68-02-2538
Task No. 3
12. SPONSORING AGENCY NAME AND ADDRESS
Environmental Protection Agency, Region 6
Air and Hazardous Materials Division
1201 Elm Street
Dallas, Texas 75270
13. TYPE OF REPORT AND PERIOD COVERED
Final 8/1/78 - 3/31/79
14. SPONSORING AGENCY CODE
906/00
15. SUPPLEMENTARY NOTES
16. ABSTRACT
This project was initiated with the overall objective of providing the Texas Air
Control Board (TACB), with a computerized emissions inventory data base for point
sources in the Houston area. This data base, when accessed by programs developed by
the TACB can be used to generate National Emissions Data System (NEDS) data reports,
to provide other emissions inventory reports useful to the TACB, and to provide point
source emissions and stack inputs for dispersion modeling studies.
Point source questionnaires were evaluated for completeness and correctness and data
were coded onto specially designed and organized screens or forms. Data from those
screens were then keypunched. Finally, computer tapes were generated from this key-
punched data and delivered to the TACB. In summary, emissions inventory data for over
2800 individual point sources were evaluated, coded, and processed.
17.
KEY WORDS AND DOCUMENT ANALYSIS
DESCRIPTORS
b.lDENTIFIERS/OPEN ENDED TERMS c. COSATI Field/Group
Texas
Emission Inventories
Point Sources
Data Handling Systems
Harris County
Brazoria County
Galveston County
NEDS
Computer Processing
18. DISTRIBUTION STATEMENT
Distribution Unlimited
CLASS (ThisReport/
Unclassified
21. NO. OF PAGES
165
20. SECURITY CLASS (Thispage)
Unclassified
22. PRICE
EPA Form 2220-1 (Rev. 4-77) PREVIOUS EDITION is OBSOLETE
165
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