vvEPA
United States
Environmental Protection
Agency
Office of Air Quality
Planning and Standards
Research Triangle Park NC 27711
EPA-450/4-82-013i
October 1982
Air
NORTHEAST CORRIDOR
REGIONAL MODELING
PROJECT
ANNUAL EMISSION
INVENTORY COMPILATION
AND
FORMATTING
Volume IX:
New York Emission Inventory
AGBNCV
This report is the result of an EPA/State/
Contractor effort and is an accurate
description of the NECRMP data base work
to date. Data revision and improvement
are expected as the Project continues, so
the contents of this document should be
considered an interim step toward the
finally modeled data base.
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EPA-450/4-82-01 SI-
NORTHEAST CORRIDOR REGIONAL
MODELING PROJECT
ANNUAL EMISSION INVENTORY
COMPILATION AND FORMATTING
Volume IX:
New York Emission Inventory
by
GCA Corporation
Bedford, MA
Contract No. 68-02-3510
EPA Project Officers: James H. Southerland
Thomas F. Lahre
Prepared For
U.S. Environmental Protection Agency
Office of Air, Noise and Radiation
Office of Air Quality Planning and Standards
Research Triangle Park, NC 27711
October 1982
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This report has been reviewed by the Office of Air Quality Planning and Standards, U.S. Environmental Protection
Agency, and approved for publication as received from GCA Corporation, Bedford, MA. Approval does not signify that the
contents necessarily reflect the views and policies of the U.S. Environmental Protection Agency, nor does mention of
trade names or commercial products constitute endorsement or recommendation for use. Copies of this report are
available from the Air Management Technology Branch, Monitoring and Data Analysis Division, Office of Air Quality
Planning and Standards, U.S. Environmental Protection Agency, Research Triangle Park, NC 27711.
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CONTENTS
Figures iv
Tables iv
1. Introduction 1
Background 1
Objectives 1
Report organization 3
2. Project History 5
Agency contacts 5
Summary of events 5
3. Point Source Inventory 8
Data procurement 8
Data review and update 8
Results 19
4. Area Source Inventory Development 29
Objectives 29
Data procurement and review 29
F)ovei^p^ont of the EIS/AS master file 33
Results 33
5. References , 40
Appendices
A. Point Source Emissions by Category for the New York Counties . 42
B. Area Source Emissions by Category for the New York Counties. . 167
C. Documentation of the Computer Routine Used for the New York
Point Source Inventory 416
D. New York Process Code—EPA SCC Code Cross Reference 420
E. Comparison of NECRMP Inventory for New York and New York Ozone
SIP Inventory 445
111
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FIGURES
Number Page
1 Boundaries of regional model grid system 2
TABLES
Number Page
1 Directory of the NECRMP Annual Regional Emission Inventory
Reports 4
2 New York Sources Listed in the RACT Directory but not in the
New York Point Source Inventory 10
3 New York Sources Listed in "Organic Chemical Producers Data
Base" but not in the New York Point Source Inventory .... 17
4 New York Point Source Emissions (1980) by Category—Statewide. 20
5 New York Point Sources (1980) Emitting More Than 100 Tons/Year
of VOC or NOX. 23
6 Area Source Categories Inventoried for New York 34
7 Annual Emissions (1980) of VOC and NOX From Area Sources in
New York 36
IV
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SECTION 1
INTRODUCTION
BACKGROUND
On a nationwide basis, nonattainment of the National Ambient Air Quality
Standard (NAAQS) for ozone is one of the most serious and widespread air
pollution problems facing the air quality management community. The Northeast
Corridor, a megalopolis of urban and suburban areas extending from Washington,
D.C. to Boston, bears a large extent of the ozone problem. The United States
Environmental Protection Agency (USEPA), in cooperation with the northeastern
states, local agencies and Metropolitan Planning Organizations (MPOs), has
undertaken the Northeast Corridor Regional Modeling Project (NECRMP) to
develop regional and urban and ozone control strategies through the use of
photochemical air quality simulation models.
To employ a regional model, an inventory of point and area source
emissions covering the entire NECRMP study area had to be assembled and placed
into a common format. Unfortunately, existing data bases were inadequate to
either properly test or validate a regional model. To this end, USEPA's
Office of Air Quality Planning and Standards retained GCA/Technology Division
to complete an annual inventory for use in NECRMP. The study area, shown in
Figure 1, includes the entire northeast quadrant of the United States from
longitude 69 degrees to 82 degrees West* and latitude 38 degrees to 45 degrees
North.
OBJECTIVES
The objective of the effort reported in this volume was to assemble the
most current, comprehensive and accurate emission inventory possible for the
State of New York. This was achieved through the cooperation of the New York
Department of Environmental Conservation (DEC) and the U.S. Environmental
Protection Agency's Region II Office. The intent of the program was to avoid
direct contact with individual facilities in New York. Rather, GCA worked
directly with the New York DEC, who in turn contacted sources when necessary.
GCA reviewed the state supplied data and submitted a list of potential errors
*The NECRMP study area also includes the Ohio Counties of Franklin, Licking,
Perry, and Fairfield. To accomodate these additional counties, the NECRMP
grid system, as shown in Figure 1, extends West to 84° longitude.
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back to the New York DEC, who was responsible for confirming the data or
supplying corrections, as necessary. The major pollutants of interest were
VOC and NOX, although TSP, SOX, and CO emissions were also compiled for
point sources. Because of this emphasis, quality assurance checks mainly
focused on sources of VOC and NOX.
The completed inventories were computerized for further use in the NECRMP
study. Point source data were computerized in the format specified in the
Emission Inventory System/Point Source (EIS/PS) user's guide-*- and area
source data were coded in Emission Inventory System/Area Source (EIS/AS)
format. *•
REPORT ORGANIZATION
The results of the NECRMP annual emission inventory are reported in an 18
volume set of documents. Volume I in this series describes the background of
the program and discusses the methods used to compile and verify the annual
emission inventory. Volumes II through XVI present a more detailed discussion
of each state's inventory effort. Volume XVII describes the spatial,
temporal, and species allocation factors developed to allow for the creation
of modeler's tapes from the completed inventory. Volume XVIII presents a
summary of the point and area source inventories for the entire study area.
Also included in Volume XVIII is a detailed analysis of the overall quality of
the data base and an assessment of the data's suitability for use in the
photochemical modeling. A directory of the NECRMP annual emission inventory
reports is presented in Table 1.
This volu.ni, -..-;,£:'-. pv:ccr.ts a detailed discussion of the annual emission
inventory for New York, consists of five sections. Section 2 describes the
project history and includes a summary of events that relate to the New York
inventory development. Section 3 discusses in greater detail the point source
inventory task while the area source inventory development is covered in
Section 4. All references cited in the volume are identified in Section 5.
Appendices A and B present county emissions for point and area sources,
respectively. The computer routine developed for use in the compilation of
the New York EIS/PS master file is presented in Appendix C. A cross reference
list matching New York process codes to EPA SCC codes is presented in
Appendix D. Appendix E presents a comparison of the final NECRMP inventory
with the New York Ozone SIP filed by NYDEC.
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TABLE 1. DIRECTORY OF THE NECRMP ANNUAL REGIONAL
EMISSION INVENTORY REPORTS
Volume
Contents
I
II
III
IV
V
VI
VII
VIII
IX
X
XI
XII
XIII
XIV
XV
XVI
XVII
XVIII
Project Approach
Connecticut Emission Inventory
Delaware Emission Inventory
Maine Emission Inventory
Maryland Emission Inventory
Massachusetts Emission Inventory
New Hampshire Emission Inventory
New Jersey Emission Inventory
New York Emission Inventory
Ohio Emission Inventory
Pennsylvania Emission Inventory
Rhode Island Emission Inventory
Vermont Emission Inventory
Virginia Emission Inventory
Washington, D.C. Emission Inventory
West Virginia Emission Inventory
Development of Temporal, Spatial
and Species Allocation Factors
Inventory Review and Evaluation
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SECTION 2
PROJECT HISTORY
AGENCY CONTACTS
The EPA Project Officer provided agency contacts in the New York
Department of Environmental Conservation (NYDEC) and the U.S. Environmental
Protection Agency's Region II office (EPA/Region II). The NYDEC contact was
responsible for confirming data, supplying required corrections or additional
data, interfacing with individual sources as necessary, and concurring on the
comprehensiveness and accuracy of the final data base-
SUMiMARY OF EVENTS
Work on the New York emission inventory occurred between March 1981 and
January 1982. GCA experienced considerable delays in receiving NYDEC's
responses to lists of questions and potential problems resulting from GCA1s
quality assurance audit of the New York inventory. The delays occurred
primarily as a result of the NYDEC's concurrent involvement in the higher
priority 1982 JI? auuinlLLal. Stuiundries of major milestones pertaining to the
New York portion of the NECRMP annual emission inventory are provided
separately for the point source and area source data as follows-
Point Sources
Work on the New Ynrk point source inventory began in March 1981 and was
completed in May 1982. Major milestones are provided as follows:
• Initial contact made with the NYDEC and a blank tape 3/19/81
forwarded for a copy of the 1980 point source data
• Preliminary 1980 point source data, in NEDS format, 5/18/81
forwarded from NYDEC to GCA
• Summary report on review of point source data 6/9/81
forwarded to EPA Project Officer, NYDEC contact
• Lists of major emitters (more than 100 TPY VOC 6/11/81
or N0x),fuel use, and all facility names from
New York inventory forwarded to Project Officer
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Cross-reference list matching NYDEC-specific process 7/7/81
codes with EPA-SCC codes forwarded from DEC
Revised 1980 point source inventory in NEDS format 2/1/82
forwarded to GCA
NEDS formatted data converted into EIS/PS format, 5/4/82
NYDEC process codes converted into SCC codes, and
EIS/PS master file forwarded to EPA Project Officer
Area Sources
Work on the New York area source inventory began in April 1981 and was
completed in January 1983. Major milestones are provided as follows:
• Area source VOC and NOX emission summaries (1980) 4/9/81
for stationary sources in the nine-county New York
City Metropolitan area forwarded to GCA
• Area source VOC emission summaries (1980) for 5/5/81
upstate New York forwarded to GCA
• GCA notified of potential errors in VOC emission 5/7/81
summaries for several upstate counties
• Area source NOX emission summaries (1980) 7/24/81
covering 11 composite categories for upstate New
York forwarded to GCA
• New York area source data reviewed and results 9/30/81
forwarded to the EPA Project Officer and EPA/
Region II contact
• Results of area source inventory review and a list 10/15/81
of uninventoried categories forwarded to the NYDEC
• 1982 ozone SIP inventory for the nine-county New 12/31/81
York City Metropolitan area forwarded from the
NYDEC to EPA/Region II
• Summary of unresolved area source inventory questions 1/29/82
forwarded to EPA/Region II contact
• GCA addressed as many unresolved problems as possible 7/30/82
based on the 1982 SIP inventory and forwarded a
summary of remaining issues to the EPA Project
Officer and EPA/Region II contact
• NYDEC provided some area source category 10/13/82
disaggregation data to EPA/Region II
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EPA/Region II forwarded the NYDEC disaggregation 10/18/82
to GCA
New York Department of Transportation (NYDOT) 10/27/82
forwarded data on weighted emission factors for
highway vehicles and vehicle miles travelled (VMT)
to EPA/Region II
NYDOT forwarded additional highway vehicle data to 11/8/82
EPA/Region II
EPA Project Officer developed factors to disaggregate 11/16/82
highway vehicle emission data into vehicle classes
and forwarded them to GCA
GCA disaggregated composite emission data into the 1/21/83
NECRMP area source categories, developed the EIS/AS
master file and forwarded it to the EPA Project Officer
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SECTION 3
POINT SOURCE INVENTORY
DATA PROCUREMENT
A computer tape containing National Emission Data System (NEDS) formatted
1980 point source emissions data for 941 facilities was supplied by the New
York Department of Environmental Conservation (NYDEC) on May 18, 1981. A
revised tape, reflecting corrections to problems discussed later in this
section, was supplied by the NYDEC on February 1, 1982. The revised tape
contained data on 1,145 facilities representing 2,564 emission points.
DATA REVIEW AND UPDATE
The New York point source data were converted into EIS/PS format and
subjected to the quality assurance (QA) checks contained in the GCA-modified
version of the NEDS-to-EIS/PS Conversion Editor.^ The data were then
subjected to the remaining QA measures in the NECRMP Annual Emission Inventory
QA program, which are described in Volume I.
One QA measure was to cross-check sources listed in the Directory of
Volatile Organic Compound (VQC) Sources Covered by Reasonably Available
Control Technology Requirements (RACT),^ the "Organic Chemical Producers
Data Base,'0 and the Emissions Inventory for the SURE Region" against
those facilities reported in the New York point source inventory. The SURE
inventory, compiled by GCA for the Electric Power Research Institute's Sulfate
Regional Experiment, reflects a 1977 base year and contains data on 6,931
facilities in New York representing 28,609 emission points, nearly 5,800 more
facilities and over 26,000 more emission points than contained in the NECRMP
data base."* Most of these facilities are believed to emit less than the
NYDEC's point source cutoff of 25 tons/year of either VOC or NOX, and
therefore would not appear in the NYDEC-supplied data. GCA concluded that it
was not practical to expect the NYDEC to respond to such a large list of
potential omissions. GCA did forward to the NYDEC lists of sources listed in
the RACT Directory^ and the Organic Chemical Producers Data Base^ that
were not identified in the New York emission inventory. The NYDEC did not
"'Although containing considerably fewer facilities, the NECRMP point source
inventory accounts for approximately 3 percent more VOC emissions and 75
percent more NOX emissions than the SURE inventory.
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provide a facility by facility accounting of the potential omissions but did
indicate that most cf the sources were believed to emit less than 25
tons/year. Sources listed in the RACT Directory^ or the Organic Chemical
Producers Data Base, but not in the NYDEC-provided inventory are provided
in Tables 2 and 3, respectively. The revised New York inventory did include
five facilities listed in the RACT Directory that had not been listed in the
original point source submittal, as indicated in Table 2. Similarly, two
facilities included in the Organic Chemical Producers Data Base that were not
listed in the original New York point source inventory were identified in the
revised point source submittal, as indicated in Table 3.
A manual review was undertaken of all sources emitting more than 100
tons/year of VOC or NOX or 500 tons/year of any criteria pollutant.
Additionally, all "error," "conditional," or "warning" messages resulting from
the conversion of data from NEDS format to EIS/PS^- format were examined.
The most significant problem with the original New York point source data
was the lack of NEDS "card 6" records for all nonboiler sources. Thus, for
all process sources, the following data were unavailable:
• source classification code (SCC)
• annual fuel, process, or solid waste operating rate
• hourly maximum de:;ign rate
• fuel sulfur content
• fuel ash content
• fuel heat content
• source description
Since the NECKMP VOC species allocation factors^ are based on SCCs, and
the point/area source inventory balance* is dependent on process rates, the
omission of this information made the original New York point source data
unsuitable for NECRMP purposes.
A number of other problems detected with the New York inventory were
determined to have been introduced when the data were converted into NEDS
format from New York's own inventory system. The most significant problems
involved the emission control equipment and efficiency fields. Upon
conversion into NEDS format, the emission control efficiency and equipment
data were not placed in the correct data fields, resulting in the rejection of
over 1,200 records by the EIS/PS system. For a number of other sources,
*As described in Volume I,-' area source fuel use is verified by subtracting
all fuel used by point sources from total fuel use reported by the Department
of Energy.
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16
-------
TABLE 3. NEW YORK SOURCES LISTED IN "ORGANIC CHEMICAL PRODUCERS DATA BASE1
BUT NOT IN THE NEW YORK POINT SOURCE INVENTORY
Source
Location
Principal products
Adhesive Products Corp.
Agway Inc.a
Newton Filaments, Inc.
Bisonite Co., Inc.
Buffalo Color Corp.3
The Dexter Corp.
Felton International, Inc.
Gladding Corp.
The Goodyear Tire & Rubber Co.
Grestco Dyes & Chemicals, Inc,
Guardian Chemical Corp.
Harstan Chem. Corp.
MacKenzie Chem. Works, Inc.
N. L. Industries, Inc.
Northeastern Labs Co., Inc.
Ruco
Bronx
Clean
Homer
Buffalo
Buffalo
Olean
Brooklyn
South Otselic
Niagara Falls
Long Island City
Hauppauge
Brooklyn
Central Islip
Niagara Falls
Melville
Hicksville
Epoxy & Polyurethane Resins,
Polyethyne Terephthalate
Resin
Urea
Nylon Monofilament,
Polyethylene Terephthalate
Fibers
Alkyds & Unsaturated
Polyester Resins
N,N-Dimethy 1aniline,
N-Methylaniline
Epoxy & Polyurethane Resins
Geraniol
Nylon Monofilament
Polyvinyl Chloride
Linear Alkylate Sulfonate
Benzamidle, Bromonaphthalene
Acetic Acid Salts
Diaminobenzoic Acid, 3, 5—
Dinitrobenzoic Acid
Acetic Acid Salts
Acrylic & Polyurethane,
Polyvinyl Acetate &
Copolymers
Polyurethane Resins
(continued)
17
-------
TABLE 3 (continued)
Source
Location
Principal products
Olin Corp.
Pennwalt Corp.
Polymer Materials, Inc.
The Procter & Gamble Co.
Ritter Chemical Co., Inc.
Robinson-Wagner Co., Inc.
Sapolin Paints, Inc.
Smith Chemical & Color
Co., Inc.
Synres Chemical Corp.
Van De Mark Chemical Co., Inc,
Conap, Inc.
R.S.A. Corp.
Rochester
Geneseo
Farmingdale
Port Ivory
Amsterdam
Mamaroneck
Brooklyn
Jamaica
Tonawanda
Lockport
Olean
Ardsley
Carbon Tetrabromide,
Polyurethane Resins,
Toluene-2,4 Diamine
Benzoyl Peroxide, Cumene
Hydroperoxide
Cellulose Acetate
Glycerol (Natural &
Synthetic)
Acetic Acid Salts, Sodium
Acetate
Hexadrecyl Alcohol
Alkyds & Unsaturated
Polyester Resins
Calcium Stearate
Phenolic Resins
Phosgene
Polyurethane Resins
Acetic Acid Salts
'included in revised inventory
18
-------
emissions estimation methods fields were blank for pollutants that were
reported in the emissions estimate fields. Those records were also rejected
by the EIS/PS system.^ Also believed to be related to data conversion
problems were the large number of points with reported stack temperatures of
8°F.
For many boiler sources, the emissions estimation method was reported as
"Code 3." Use of Code 3 indicates that the emissions are to be computer-
calculated using emission factors in the SCC listings contained in either the
NEDS or EIS/PS system. When Code 3 is used, the computer will automatically
calculate emissions estimates, overriding any data reported in the
corresponding emission estimate fields. For several boiler sources, the
percent sulfur and ash content fields were blank although the estimation
method was "Code 3." Omission of any field necessary for emissions
calculation (process rate, valid SCC, sulfur content, ash content) causes the
EIS/PS system to replace the emissions estimate field with zero.
GCA forwarded a comprehensive accounting of all questions, missing data,
problems, or suspected errors resulting from the point source QA review to the
EPA Project Officer and the New York DEC on June 9, 1981.
Since the New York DEC utilizes its own process codes in preference to
the EPA SCC codes, it was necessary to devise a means to convert the New York
Process Codes into SCCs. At the June 26, 1981 NECRMP Interagency Coordination
Group Meeting in Philadelphia, the New York DEC contact reported that a
cross-reference list matching the New York Process Codes with the most
appropriate EPA-SCC codes had been compiled. This cross-reference list was
forwarded to GCA On July 7, 1981. GCA developed a PL/1 computer routine to
convert the New York Process Codes to SCCs using the DEC-supplied cross
reference list. The computer routine is presented in Appendix C, while the
cross-reference list is reported in Appendix D.
On February 1, 1982, the New York DEC forwarded a revised 1980 point
source inventory that addressed the most serious data conversion problems
presented earlier in this section. As agreed, the revised tape contained Card
6 records for all sources with the New York Process Codes included in the
"comments" field. GCA converted the process codes to the appropriate SCCs
using the computer routine and cross reference list discussed previously. The
NEDS formatted data were then converted into EIS/PS format.
RESULTS
For reporting purposes, point source emissions for New York were
aggregated into 70 categories based on specific SCC-SIC combinations. A
complete description of the codes used to aggregate emissions is presented in
Volume I.-* For points with multiple SCCs, no attempt was made to split
emissions into more than one category. In these instances, the primary SCC
was used to account for all emissions at that point.
Statewide point source emissions for 1980 are presented, by category, in
Table 4. County-specific point source emissions are presented, by category,
in Appendix A.
19
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A list of "major" facilities was developed by totalling emissions at each
facility using criteria of 100 tons/year of VOC or NOX to define a major
source. These facilities, and their reported 1980 emissions for all five
criteria pollutants, are presented in Table 5. A comparison of the emission
totals in Tables 4 and 5 shows that 97.5 and 99.1 percent of point source VOC
and NOX, respectively, originate from major VOC and NOX emitters. A
correspondingly high (95.6) percentage of point source S02 is discharged
from major point sources of VOC and NOX. Conversely, only 43.7 percent of
TSP and 59.3 percent of CO are emitted from major point sources of VOC and
NOX.
The completed New York point source inventory was written onto computer
tape for delivery to EPA. Included on the tape, which was forwarded on May 4,
1982 were the following files:
• EIS/PS Master File (1980)
• NEDS (1980) (converted from EIS/PS masterfile)
Further evaluation of the New York emission inventory and improvements
made can be found in Volume XVIII of the NECRMP Annual Emission Inventory
Series, and Appendix D of this report.
22
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28
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'SECTION 4
AREA SOURCE INVENTORY DEVELOPMENT
OBJECTIVES
The area source emission inventory task entailed reviewing area source
inventories prepared by the states for technical accuracy and consistency with
EPA-prescribed procedures and developing these area source inventories where
state-developed inventories were unavailable. The major objective of this
effort was to ensure that all emissions of VOC and NOX were accounted for
and that the procedures used to develop the inventories were consistent from
state to state. It was also important that the inventories be disaggregated
into sufficient categories to allow for application of temporal and pollutant
allocation factors and the evaluation of control scenarios in subsequent
modeling efforts.
DATA PROCUREMENT AND REVIEW
The 1980 VOC and NOX area source emissions summaries for the
nine-county Ne- Yrr'r ^*-y M?nrop^litan Area were forwarded to GCA by the NYDEC
on April 9, 1981. The NYDEC sent GCA summaries of area source emissions of
VOC for the remaining 53 counties on May 5, 1981. On May 7, 1981, GCA was
notified of potential errors in the VOC emissions summary for several upstate
counties. GCA received cne upstate NOX emissions summary on July 24, 1981
from the NYDEC.
The above area source inventories were reviewed for comprehensiveness and
consistency with the area source methodologies presented in Volume I.-* GCA
identified several data gaps and inconsistencies that hindered use of the New
York data for NECRMP purposes, which are discussed as follows. A number of
composite categories needed to be disaggregated to conform to the list of area
source categories being used in NECRMP. Emission factors and activity rates
were not provided for the majority of categories. GCA also identified
discrepancies with some of the emission factors that were provided by the
NYDEC.
GCA eventually chose not to utilize the upstate NOX emissions summary
for the following reasons. First, the emissions were aggregated into
composite categories. Although the NYDEC later disaggregated the VOC
emissions summaries into the appropriate NECRMP categories, no information was
provided to enable proper ctisaggregation of the NOX emissions.
Additionally, tue inventory was reportedly based on Part 208 Water Quality
Management Program population projections, which were determined to vary
significantly from the 1980 Census data used in all other NECRMP states.
29
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The results of GCA's review of the area source data were forwarded to the
EPA Project Officer and EPA/Region II contact on September 30, 1981 and to the
NYDEC on October 15, 1981.
The 1982 Ozone SIP inventory for the nine-county New York City
Metropolitan Area was forwarded from the NYDEC to EPA/Region II on December
31, 1981 and provided to GCA shortly thereafter. As of January 29, 1982, GCA
had not received responses to the list of questions concerning the NYDEC
inventory and at the request of the Project Officer, forwarded another letter
to the EPA/Region II contact summarizing the unresolved problems. GCA
addressed as many problems as possible based on the 1982 SIP inventory and
forwarded a summary of remaining issues to the EPA Project Officer and
EPA/Region II contact on July 30, 1982.
NYDEC provided VOC disaggregation data to EPA/Region II which was in
turn forwarded on October 18, 1982. On November 16, 1982, GCA received
NYDOT-supplied VMT data, and factors to disaggregate highway vehicle emissions
data into the appropriate vehicle classes from the EPA Project Officer.
In some instances, GCA had to develop emission factors, activity rates,
and/or emissions for various categories to supplement the New York DEC
supplied data. This was necessary to meet the requirements of the EIS/AS
system and, in some cases, to be more consistent with Volume 1^
methodologies. The specific categories to which this applies are discussed
below in detail.
Upstate Inventory
Gasoline Handling—
GCA back-calculated the total quantity of gasoline marketed for stage I
gasoline evaporation, stage II gasoline evaporation, and storage tank .
breathing using the appropriate AP-42 emission factors.° The emission
factor for stage I gasoline evaporation was based on the assumption that
25 percent of the New York service stations utilize splash loading and the
remaining 75 percent employ submerged filling.9 Derivation of this
composite emission factor is further explained in Volume I. The gasoline
sales figures were then applied to the NYDEC-supplied tank truck loading and
transit VOC emissions to back-calculate the VOC emission factors, which were
found to vary slightly from county to county.
Degreasing—
GCA utilized an emission factor of 2000 Ib/ton of degreasing solvent to
back-calculate activity rates from the NYDEC-supplied emission estimates.
Architectural Surface Coating and Automobile Refinishing—
To maintain consistency with the other NECRMP states' inventories, GCA
calculated VOC emissions using the 1980 Census of Population-^ with per
capita emission factors derived from Volume I of the Procedures for
Preparation of Emission Inventories for Volatile Organic Compounds.*
30
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Small Industrial Surface Coating—
All industrial surface coating emissions were assumed to be covered in
the upstate New York point source inventory.
Graphic Arts—
GCA verified that the DEC-provided emission totals yielded the EPA
recommended factor of 0.8 Ib/capita^ when divided by the 1980 population-^
for each county.
Commercial/Consumer Solvent Use—
GCA attempted to duplicate the DEC's emissions estimates for this
category using the 1980 Census of Population^ and the EPA recommended
factor of 6.3 Ib/capita. The GCA calculated emissions estimates varied
slightly for those reported by the DEC. To enable entry into EIS/AS, GCA
utilized a factor of 2000 Ib solvent/ton of VOC emissions to back calculate
activity levels.
Cutback Asphalt—
The DEC provided an estimate of VOC emissions from asphalt application
but did not provide activity rates or emission factors. To enable entry into
EIS/AS, GCA utilized a factor of 2000 Ib of solvent/ton of VOC emissions to
back calculate activity levels.
Highway Vehicles—
The DEC provided vehicle class-specific VOC and NOX emissions for the
nine-county New York City Metropolitan Area, but only provided composite VOC
and NOX emissions for upstate New York. VMT data were obtained from the
NYDOT. The EPA Project Officer provided factors to disaggregate the composite
VOC emissions into the appropriate vehicle classes. Emission factors were
back-calculated from the vehicle class-specific emissions and VMT data.
Vehicle class-specific NOX emissions for the upstate inventory were
calculated using the vehicle class specific ratios of VOC to NOX emissions
from the Metropolitan New York City inventory.
Residential and Commercial/Institutional Fuel Use—
Fuel usage rates were back-calculated from the DEC provided emissions
totals and emission factors. Use of wood in both sectors was assumed to be
negligible.
Industrial Fuel Use—
The DEC did not provide information on area source industrial fuel use
emissions which were assumed to be adequately covered in the point source
inventory.
Aircraft—
VOC emissions provided by the state, and composite VOC emission factors
for civil, commercial, and military aircraft, obtained from EPA/NADB,^2 were
used to back-calculate the aircraft landing and takeoff (LTO) data.
Correspondingly, NOX emission factors from EPA/NADB,^2 were then used to
calculate the NOX emissions for civil, commercial and military aircraft.
31
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Railroad Locomotives—
VOC emissions provided by the state were used with the appropriate AP-42
VOC emission factor" to back-calculate the activity rates. NOX emissions
were then derived using the appropriate NOX emission factor from AP-42.^
Vessels-Gasoline—
Since neither emission factors nor activity rates were provided by the
NYDEC, GCA utilized the VOC and NOX emission factors derived by GCA for the
NECRMP area source inventory for Ohio-'--'- to back-calculate activity rates for
each county.
Vessels-Distillate—
GCA back-calculated activity rates utilizing the emissions estimates
provided by the NYDEC, and the appropriate emission factors from the AP-42.^
Off-Highway Vehicles—
Using the NYDEC-provided emission totals, for gasoline and diesel
vehicles, and the composite emission factors from AP-42, GCA was able to
determine the activity rates for both the diesel and gasoline categories.
Onsite Incineration, Structural Fires, and Field/Slash Burning—
Emissions totals provided by the NYDEC were used in conjunction with the
appropriate AP-42 emission factors" to back-calculate activity rates.
Open Burning and Forest Fires—
GCA back-calculated activity rates utilizing the emissions estimates and
emission factors provided by the NYDEC.
Metropolitan New York City Inventory
Gasoline Handling—
The Metropolitan Uew York inventory did not include evaporative losses
from tanker truck loading and transit which were calculated by GCA using the
state-provided gasoline sales data and the appropriate EPA emission factor.^
Small Industrial Surface Coating—
GCA assumed this category to be adequately covered in the point source
inventory.
On-Highway Vehicles—
VOC and NOX emissions estimates and vehicle miles travelled (VMT), data
provided by the NYDEC, were used to back-calculate the appropriate emission
factors.
Aircraft—
Aircraft emissions were disaggregated based on the distribution of
emissions in the upstate inventory for civil, commercial, and military
aircraft. Composite emission factors, which were obtained from EPA/NADB,H
were used to baoK-ual>_uIaL.e the landing and takeoff (LTO) estimates.
32
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Railroad Locomotives—
GCA back-calculated activity rates from the NYDEC-provided emissions
estimates and appropriate AP-42 emission factors.
Vessels—
Emissions from gasoline, distillate, and residual oil powered vessels are
reported in a single composite category (vessels-gasoline). The DEC was
unable to disaggretate the composite vessel emissions estimate for the above
three categories.
Off-Highway Vehicles—
Gasoline and diesel emissions (VOC and NOX) from off-highway vehicles
were disaggregated based on the distribution of emissions in the upstate
inventory.
Onsite Incineration, Open Burning, Sturctural Fires,
Field/Slash Burning, and Forest Fires—
GCA disaggregated the reported composite emissions for these five
categories based on the distribution of emissions in the upstate inventory.
DEVELOPMENT OF THE EIS/AS MASTER FILE
After emissions were verified for all area source categories on a
countywide basis, the completed inventory was coded and keypunched in EIS/AS
format and subjected to the series of computerized QA checks included in the
EIS/AS System.^ The completed master file was then manually verified for
accuracy before the finalized data were written onto computer tape for
delivery to EPA.
Table 6 presents a list of the area source categories included in the New
York portion of the NECRMP inventory. Also identified for each category is
the type of VOC represented by the emission factor (total or reactive).
RESULTS
Statewide totals of VOC and NOX emissions from area sources in New York
are provided in Table 7. Countywide summaries are presented in Appendix B.
33
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TABLE 6. AREA SOURCE CATEGORIES INVENTORIED FOR NEW YORK
EIS/AS
Category No.
001
002
003
004
005
006
007
008
009
010
Oil
012
013
014
015
016
017
018
019
020
021
022
023
024
025
026
027
028
Category description
Stage I Gasoline Evaporation
Stage II Gasoline Evaporation
Storage Tank Breathing
Gasoline Loading/Transit
Small Industrial/Commercial Degreasing
Dry Cleaning
Architectual Surface Coating
Automobile Refinishing
Small Industrial Surface Coating
Graphic Arts
Commercial /Consumer Solvent Use
Cutback Asphalt*
Pesticides
On-Highway Light-Duty Vehicles
On-Highway Light-Duty Trucks — Class I
On-Highway Light-Duty Trucks — Class II
On-Highway Heavy-Duty Gas Trucks
On-Highway Heavy-Duty Diesel Trucks
On-Highway Motorcycles
Residential Anthracite Coal
Residential Bituminous Coal
Residential Residual Oil
Residential Distillate Oil
Residential Natural Gas
Residential LPG
Residential Wood
Commercial /Institutional Anthracite
Commercial /Institutional Bituminous
Pollutants
inventoried
TVOC
TVOC
TVOC
TVOC
RVOC
RVOC
RVOC
RVOC
TVOC
RVOC
RVOC
RVOC
RVOC
RVOC NO
X
RVOC NO
X
RVOC NO
X
RVOC NO
X
RVOC NO
X
RVOC NO
X
TVOC NO
X
TVOC NO
X
TVOC NO
X
TVOC NO
X
TVOC NO
X
TVOC NO
X
RVOC NO
X
TVOC NO
X
TVOC NOX
(continued)
34
-------
TABLE 6 (continued)
EIS/AS
Category No.
029
030
031
032
033
034
035
036
037
038
039
040
041
042
043
044
045
046
047
048
049
050
051
052
053
054
Category description
Commercial/Institutional Residual Oil
Commercial/Institutional Distillate Oil
Commerc ial/ Institutional Natural Gas
Commercial/Institutional LPG
Commerc ial /Institutional Wood /Other
Industrial Anthracite
Industrial Bituminous
Industrial Residual Oil
Industrial Distillate Oil
Industrial Natural Gas
Industrial LPG
Industrial Wood/Other
Military Aircraft
Civil Aircraft
commercial Aircraft
Railroad Locomotives
Gasoline-Powered Vessels
Distillate Oil-Powered Vessels*
Residual Oil-Powered Vessels*
Off-Highway Vehicles—Gas
Off-Highway Vehicles — Diesel
Onsite Incineration
Open Burning
Structural Fires
Field/Slash Burning
Forest Fires
Pollutants
inventoried
TVOC NO
X
TVOC NO
X
TVOC NO
X
TVOC NO
X
TVOC NO
X
TVOC NO
X
TVOC NO
X
TVOC NO
X
TVOC NO
X
TVOC NO
X
TVOC NO
X
TVOC NO
X
TVOC NO
X
TVOC NO
X
TVOC NO
X
TVOC NO
X
TVOC NO
X
TVOC NO
X
TVOC NO
X
TVOC NO
X
TVOC NO
X
TVOC NO
X
TVOC NO
X
TVOC NO
X
TVOC NO
X
TVOC NOX
*Not included in "city" inventory
35
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SECTION 5
REFERENCES
10.
McMaster, Larry M. Emission Inventory System/Point Source Users Guide,
EPA-450/4-80-010. May 1980.
McMaster, Larry M. Emission Inventory System/Area Source Users Guide,
EPA-450-/4-80-009. May 1980.
Sellars, F. M., M. J. Geraghty, A. M. Kiddie, B. J. Bosy, and S. V.
Capone. Northeast Corridor Regional Modeling Project—Annual Emission
Inventory Compilation and Formatting. Volume I: Project Approach.
GCA/Technology Division, Bedford, MA for the U.S. Environmental
Protection Agency. EPA-450/4-82-013a. August 1982.
Mehta, Dilip H., and John E. Spessard. Directory of Volatile Organic
Compound (VOC) Sources Covered by Reasonably-Available Control Technology
Requirements. EPA-450/4-80-007. February 1981.
Radian Corp. "Organic Chemical Producers Data Base" prepared for U.S.
EPA/OAQPS. December 1979.
Klemm, H. A. and R. J. Brennan. Emissions Inventory for the SURE
Region. GCA/Technology Division, Bedford, MA for the Electric Power
Research Institute. EPRI-EA-1913. April 1981.
Sellars, F. M., M. J. Geraghty, A. M. Kiddie, B. J. Bosy, and S. V.
Capone. Northeast Corridor Regional Modeling Project—Annual Emission
Inventory Compilation and Formatting. Volume XVII: Development of
Temporal, Spatial, and Species Allocation Factors. GCA/Technology
Division, Bedford, MA for the U.S. Environmental Protection Agency.
EPA-450/4-82-013q. January 1983.
Compilation of Air Pollutant Emission Factors, AP-42. 3rd Edition and
subsequent supplements, U.S. Environmental Protection Agency, Research
Triangle Park, NC. August 1977.
Lamason, W. H., II and T. F. Lahre. Procedures for the Preparation of
Emission Inventories for Volatile Organic Compounds. Volume I, Second
Edition. (EPA-450/2-77-028, 2nd Edition.) September 1980.
U.S. Department of Commerce, Bureau of the Census. 198Q Census of
Population. U.S. Government Printing Office, Washington, D.C. 1981.
40
-------
11. Haupt, S. E., F. M. Sellars, M. J. Geraghty, A. M. Kiddie, B. J. Bosy,
and R. D. Green. Northeast Corridor Regional Modeling Project—
Annual Emission Inventory. Volume X: Ohio Emission Inventory.
EPA-450/4-82-013J. October 1982.
12. Mann, Charles 0. EPA/OAQPS—NADB. Personal communication with Frederick
M. Sellars, GCA/Technology Division. March 10, 1981.
41
-------
APPENDIX A
POINT SOURCE EMISSIONS BY CATEGORY FOR THE NEW YORK COUNTIES
Table A-l presents point source emissions, by category, for each of the
New York counties, which are identified below.
County
Albany
Allegany
Bronx
Broome
Cattaraugus
Cayuga
Chautauqua
Chemung
Chenango
Clinton
Columbia
Cortland
Delaware
Dutchess
Erie
Essex
Franklin
Fulton
Genesee
Greene
Hamilton
Herkimer
Jefferson
Kings
Lewis
Livingston
Madison
Monroe
Montgomery
Nassau
New York
NEDS/EIS County Code
0060
0120
0600
0640
0840
0860
1000
1060
1080
1120
1220
1400
1520
1620
2000
2020
2240
2340
2400
2660
2820
2960
3340
3440
3740
3880
4040
4380
4400
4520
4660
County
Niagara
Oneida
Onondaga
Ontario
Orange
Orleans
Oswega
Otsego
Putnam
Queens
Rensselaer
Richmond
Rockland
St. Lawrence
Saratoga
Schenectady
Schoharie
Schuyler
Seneca
Steuben
Suffolk
Sullivan
Tioga
Tompkins
Ulster
Warren
Washington
Wayne
Westchester
Wyoming
Yates
NEDS/EIS County Code
4720
5060
5100
5120
5140
5180
5240
5260
5640
5660
5700
5720
5780
5930
5965
6040
6060
6080
6160
6500
6580
6600
6700
6720
6840
7040
7100
7240
7320
7580
7600
42
-------
1. POINT SOURCE EMISSIONS (1980) FOR THE NEW YORK COUNTIES
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