United States
Environmental Protection
Agency
Office of Air Quality
Planning and Scandards
Research Triangle Park NC 2771
EPA-450M-39-OCS
MAY 1989
DEVELOPMENT OF A BASE YEAR
ANTHROPOGENIC EMISSIONS
INVENTORY
Sg^^
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EPA-450/4-89-008
REGIONAL OZONE MODELING FOR
NORTHEAST TRANSPORT
DEVELOPMENT OF A BASE YEAR
ANTHROPOGENIC EMISSIONS
INVENTORY
BY
ALLIANCE TECHNOLOGIES CORPORATION
RESEARCH TRIANGLE PARK, NC 27709
EPA CONTRACT NO. 68-02-4396
EPA PROJECT OFFICER: EDWIN L. MEYER, JR.
OFFICE OF AIR QUALITY PLANNING AND STANDARDS
U. S. ENVIRONMENTAL PROTECTION AGENCY
RESEARCH TRIANGLE PARK, NC 27711
MAY 1989
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DISCLAIMER
This report was furnished to the U.S. Environmental Protection Agency by-
Alliance Technologies Corporation, 100 Europa Drive, Chapel Hill, North
Carolina, 27514, in fulfillment of Contract No. 68-02-4396, Task No. 23. The
opinions, findings, and conclusions expressed are those of the authors and not
necessarily those of the U.S. Environmental Protection Agency. Mention of
company or product name is not to be considered as an endorsement by che U.S.
Environmental Protection Agency.
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ACKNOWLEDGEMENTS
A number of groups participated in the ROMNET Emissions Committee,
providing guidance and information that was critical in the development of the
1985 ROMNET inventory. Committee members included staff from State air
pollution agencies, as well as a number of EPA offices and laboratories: the
Office of Air Quality Planning and Standards, the Office of Mobile Sources,
the Air and Energy Environmental Research Laboratory, and the Atmospheric
Research and Exposure Assessment Laboratory. In addition, individuals
involved in developing the 1985 National Acid Precipitation Program (NAPAP)
and National Emissions Data System (NEDS) inventories, which were precursors
to the ROMNET inventory, provided much needed information and support. The
authors wish specifically to thank Norman Possiel, the ROMNET Technical
Coordinator, Edwin Meyer, the Project Manager, and Keith Baugues, the
Emissions Committee Chairman, for their technical guidance.
111
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TABLE OF CONTENTS
1. INTRODUCTION 1
2. OVERVIEW OF EMISSIONS DATA 3
Structure of the Inventory 3
Emission Summaries 4
3. EVOLUTION OF THE ROMNET BASE YEAR INVENTORY 11
Parent Emissions Inventories 11
NAPAP Emissions Allocation Methodologies 12
Methodologies Developed and Modifications Made under ROMNET . . 14
4. SPECIATION OF VOC TO CARBON BOND IV REACTIVITY CLASSES 16
5. QUALITY CONTROL 20
Quality Control of the Parent NAPAP Inventory ... 20
Quality Control Efforts under ROMNET 21
6. MOBILE SOURCE ADJUSTMENT v 26
Adjustment Methodology . . . > 29
Inputs for the Adjustment 36
Analysis and Rejection of Speed Adjustments 38
7. AREA SOURCE ADJUSTMENTS 42
Gasoline Marketing and Bulk Gas Terminals and Plants 44
Gasoline Vessels Architectural Coating and Miscellaneous
Solvent Use 45
Hazardous Waste Treatment, Storage, and Disposal Facilities . . 47
REFERENCES 48
APPENDIXES
A. State and Province Emissions for a Typical Summer Weekday
B. Carbon Bond IV Species Assignments used in ROMNET
C. Changes Made as a Result of CO Quality Control
D. Composite Mobile Source Emission Factors for Different
Temperatures
IV
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LIST OF FIGURES
1. ROMNET Region 2
2. Spatial Variation of VOC for a Summer Weekday 7
3. Hourly Variation of VOC Emissions for a Summer Weekday .... 8
4. Hourly Variation of NOX Emissions for a Summer Weekday .... 9
5. Hourly Variation of CO Emissions for a Summer Weekday 10
6. Summary of Software Modules and Input Data Used in FREDS ... 13
7. VOC Speciatibn Methodology 16
3. Effect of Average Daily Temperature on VOC Emissions 27
9. Effect of Diurnal Temperature Range on VOC Emissions 28
10. VOC Emissions Per Fuel Consumed 41
LIST OF TABLES
1. Summer Weekday Emissions by Source Category for
the U.S. Portion of the ROMNET Domain 5
2. Partial List of Carbon Bond IV Assignments 18
3. Revised Summer Allocation Factors for Area Source Categories . . 43
v
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SECTION 1
INTRODUCTION
Control strategies to attain the ozone National Ambient Air Quality
Standard (NAAQS) are complicated by the transport of ozone and ozone
precursors from one urban area to another. Pollutant transport is especially
pronounced in the Northeastern United States, where several urban areas are in
close proximity to one another. In order to quantify the concentrations of
pollutants transported among urban areas and to identify and assess strategies
for attaining the ozone NAAQS in the Northeast, the U.S. Environmental
Protection Agency is undertaking a program of Regional Ozone Modeling for
Northeast Transport (ROMNET) . Figure 1 shows the area covered by the ROM-NET
program. This region includes 12 full States and the District of Columbia,
portions of another 7 States, and a portion of Ontario, Canada.
A
ROMNET will examine three types of emission scenarios: base year
emissions, future year emission projections, and projections of emissions
under different control strategies. The base year for ROMNET is 1985, ana two
projection years will be studied: 1995 and 2005. A detailed emission
inventory is being prepared for each scenario to serve as input to the
Regional Oxidant Model (S.OM) .
Inventory development for ROMNET has been overseen by an Emissions
Committee made up of representatives of EPA and the States in the region.
State representatives on the committee have provided State-specific input to
the inventories, and the committee has reviewed and contributed to the
development of the overall methodologies used in compiling the inventories.
This report describes the preparation of the ROMNET base year (1985)
emission inventory. Section 2 gives an overview of the emissions data in the
inventory, and Section 3 gives an overview of the evolution of the base year
inventory. Section 4 discusses VOC speciation in the ROMNET inventory;
Section 5 discusses quality control efforts; and Sections 6 and 7 describe
adjustments that were made to give mobile and area source emission estimates
representative of the temperatures and weather conditions during ozone
episodes. Development of projection and control strategies inventories will
be described in future reports.
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**W -J/£T\
'7^73'-y'vr i i *j .? V
->-X-
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SECTION 2
OVERVIF* oF £IiI5oIGNS
The ROMNET inventories give emissions data for tonal hydroc.irbor.s (TliC) ,
volatile organic compounds (VOC) , nitrogen oxides (NOX) , and carbon monoxide (CO) ,
which are orecursors in tropoapheric -/-one formation. :;G, -j-aisslons --r~ :lvid='.;.
into NO and NO,; and VOC emissions are broker, into 11 reacci'/ity classes' o Is fir.
(OLE), paraffin (PAR), toluene (TOL) , xyienb XYL; , formaicenyce , .rCL\M', . ccr.ej
aldehydes (ALD2) , ethylene (£TH). isoprsns .'[50), -.onre.icciva . -'.PC. . zscnana
(METH) , and mechanol (MTHL).1 VOC classifications are based on the Carbon Eond IV
system, discussed in more detail in Section 4. Emission rates have been adjusted
to reflect emissions on clear hot summer days, which characterize a typical
episode with exceedences of the ozone NAAQS . . The base year inventory discussed in
chis report gives emissions data for 1985.
STRUCTURE OF THE INVENTORY
Anthropogenic emissions data are provided separately for point sources.
stationary area sources, and mobile sources. Point sources include all emission
sources that are handled on an individual po LUC basli in ZPA'i :»aci-jnal luiissions
Data System (NEDS). The goal of NEDS was to collect data on all plants emitting
100 tons per year or more of any cricaria pollutant '"OC, ::TO , ;JO-, particulars
matter, or lead).
The area source inventory does not address individual sources, but instead
gives emissions for aggregated groups of sources that are too small or numerous ^.z
be covered by the point source inventory. Area sources in the ROMNET inventory-
include minor fuel combustion sources; open burning and solid waste disposal;
structural and forest fires; non-highway transportation sources, such as trains,
airplanes and off-highway vehicles; jol/ant =v-apo^acijn fi'c;.i paints ana .^cr.= i
solvent uses; and some industrial fugitive emissions and process vent emissions.
The mobile source inventory includes aggregates of only hizh"a.v vehicle err.ijsior.s.
Both the mobile and stationary area source inventories Ir.ciuda thrse sap.-rntre
computer files reflecting weekday, Saturday, and Sunday emissions. Each fila
contains hourly emission profiles for the 15 pollutant categories listed above.
The mobile source files further classify VOC emissions into evaporative emissions
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rrora gasoline vehicles, exhaust emissions frcm gasclir.e vih_ei=s. aud C:-:.-._LUJ •_
emissions from diesels (evaporation emissions iirom uicse.i.a die n&gi 1.510 j.c;.
Emissions in these files are apportioned into a Mercator grid, system, with each
grid-square covering one-si:-:th ;? .4 iegrse latitude and one--fourth ~: • d.^gr3£
longitude (or an area roughly 20 km by 20 km). The mobile source inventory also
apportions emissions by Staca and county.
The point source inventory ;.s consolidated into a single file, with hourly
allocation factors for all of ens chrse aay- "ypas. The Jil-e ilso ^ive.s j~e
location of eacr. source, a^ong '"itr- Jtnar c-er~ir.er.t aata ;ucn as smisoior; .:s".ght
ana temperature, operating rats, source classification code (SCC), ana Standard
Industrial Classification (SIC) .
EMISSION SUMMARIES
Table 1 gives typical summer weekday emissions of VOC, NO , and CO in ;he
United States portion of the ROMNET region, broker, down by emission sourca
categories. Emissions in the table include temperature and weather adjustments
for mobile and area source categories, as well as adjustments for changes in the
MOBILE emission model (Sections 6 and 7). Unadjusted emissions are also shown.
Highway mobile source amissions were adjusted -:G a daily average camperati-.r^
of 85°F. This adjustment, along with the addition of running losses and revision
of evaporative losses, resulted in i 22 "ercsnt Lncrsass "In CO. ~n .3 percent
decrease in NO, and a 37 percent increase in VOC from highway vehicles. With the
adjustments, highway sources account for about 74 percent of CO emissions, 34
percent of NOX emissions, and 40 percent of VOC emissions in the United States •
portion of the ROMNET region. VOC emissions from other area sources, which
increased by about 12 percent overall as a result of temperature and weather
adjustments, account for about 52 percent of VOC emissions in the region.
Appendix A gives a more aecai^ia -^raaKCCwr, ^c oiiiu^ions oy Jcacs O.UG. .or ^:i=
Canadian Province of Ontario.
Figure 2 illustrates the spatial variation of VOC emissions across the ROMNET
domain. Patterns for CO and MO. are similar. Tisura ? snows ~he hourly •"•.ariatior.
A ""
of total VOC emissions as well as point, area, mobile components for a 7v-?i.:al
summer weekday. Figures 4 and 5 show hourly variations for N0x and CO emissions,
respectively.
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TABLE 1. SUMMER WEEKDAY EMISSIONS 3Y SOURCE CATEGORY FOR
THE U.S. PORTIO.'f OF TEE ECMNET DOMAIN •'tons/dav's
Unadjusted (NAPAP)
CO NOx VOC
POINT SOURCES
Fuel Combustion
Utility External - Coal
Utility External - Oil
Utility External - Gas
Utility External - Other
Utility Internal - Oil
Utility Internal - Gas
Industrial External - Oil
Industrial External - Gas
Industrial External - Other
Industrial Internal - Oil
Industrial Internal - Gas
Commercial/Institutional
Aircraft (Internal)
Solvent Metal Cleaning
Printing and Publishing
Dry Cleaning
Automobile Surface Coating
Beverage Can Surface Coating
General Wood Surface Coating
Paper Surface Coating
Miscellaneous Surface Coating
Crude oil & gasoline storage
Bulk gasoline storage
Marine Vessel Loading
Service Stations - Stage I
Chemical Manufacture Vents
Chemical Manufacture Fugitives
Petroleum Refinery Fugitives
Refinery Wastewater Treatment
Refinery Vacuum Distillation
Cellulose Acetate Manufacture
Styrene- Butadiene Rubber Mfg.
Polyethylene Manufacture
Vegetable Oil Processing
Paint and Varnish Manufacture
Rubber Tire' Manufacture
Carbon Black Manufacture
Coke Oven Byproduct Plants
Other Industrial 2
Waste Disoosal
TOTAL - POINT SOURCES 3
HIGHWAY MOBILE SOURCES 30
176
38
15
5
4
2
26
58
4
0
70
21
143
1
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
289
0
0
0
0
0
0
148
17
,261
131
,410
,414
5,721
414
176
7
14
8
131
146
6
9
613
62
10
1 0
0
0
0
7
0
0
0
0
0
0
0
30
0
0
0
19
0
0
13
0
0
0
0
11
425
32
7,851
6.223
23
10
0
1
1
0
12
12
1
0
5
3
6
34
131
0
140
64
30
85
344
67
19
13
1
1
9
16
9
18
30
4
30
2
19
11
2
20
744
3
1,926
6.546
Adiusted
CO
176
33
15
3
4
2
25
53
4
0
70
21
143
1
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
289
0
0
0
0
0
0
143
17
2,261
131
3,410
37.016
NOx
5,721
414
176
7
14
8
131
146
6
9
613
62
10
0
0
0
0
7
0
0
0
0
0
0
0
30
0
0
0
19
0
0
13
0
0
0
0
11
425
32
7,851
5.108
VOC
23
10
0
L
1
0
12
12
1
0
5
3
6
34
131
0
140
64
30
85
344
67
19
13
I
1
9
16
9
18
30
4
- r
2
19
11
2
20
744
3
1,926
8,956
(continued)
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TABLE 1. SUMMER WEEKDAY EMISSIONS BY SOURCE CATEGORY FOR
THE U.S. PORTION OF THE ROMKST DOMAIN (tons/day)
Unadjusted (
NON- HIGHWAY AREA SOURCES
Residential Fuel - Wood
Residential Fuel - Other
Commercial/Institutional Fuel
Industrial Fuel - Coal-
Industrial Fuel - Oil
Industrial Fuel - Gas
Incineration - Residential
Incineration - Other
Open Burning - Residential
Open Burning - Other
Off-Highway Vehicles
Railroad Locomotives
Aircraft
Vessels - Gasoline
Vessels - Other
Forest Wildfires
Structural Fire
Gasoline Marketed
Degreasing
Drycleaning
Graphic Arts/Printing
Rubber and Plastic Manufacture
Surface Coating
Architectural
Auto Body Repair
Motor Vehicle Manufacture
Paper Coating
Fabricated Metals
Machinery Manufacture
Furniture Manufacture
Flat Wood Products
Other Transportation Equip.
Electrcal Equipment
Ship Building/Repair
Misc. Industrial Manufacture
Misc. Industrial Solvent Use
POTWs
Cutback Asphalt Paving
Chemical Manufacture Fugitives
Bulk Terminals and Bulk Planes
Petroleum Refinery Fugitives
Process Emissions - Bakeries
Process Ems. - Pharmaceuticals
Process Ems.- Synthetic Fibers
Crude Oil/Gas Prod. Fields
Hazardous Waste TSDFs
TOTAL - OTHER AREA SOURCES
TOTAL - POINT. MOBILE. AREA
CO
556
13
28
14
12
76
703
54
886
13
5,391
113
600
333
35
90
258
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
9, 191
43.014
NOx
7
36
146
111
64
440
3
17
53
1
706
322
84
4
69
\ 3
6
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
2,072
16 . 1&6
NAPAP)
voc
121
2
4
0
3
5
46
5
279
3
631
78
99
95
17
12
47
873
495
319
280
590
571
222
58
340
107
51
89
15
3
14
11
347
2,230
11
130
195
263
301
48
45
93
70
656
10,433
18.905
CO
556
18
28
14
12
76
703
54
886
18
5,391
113
600
573
35
90
258
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
9,426
^9.351
Adi us ted
NOx
7
36
146
111
64
440
T
J
i_y
53
I
706
322
84
7
£9
3
6
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
2,075
15.035
VOC
121
2
4
0
3
5
46
5
279
5
681
78
99
161
17
12
47
1,298
495
319
280
590
1,054
222
58
340
107
51
89
15
3
14
11
347
2.230
11
130
195
405
301
48
/. -
-i- _J
93
70
787
11,676
22.557
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"3
CO
c
(T>
M
(U
rt
111
1
H«
D>
-J O
D
O
n
n>
rc
t
x TOMS/I l.djR/KM
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0 -
"i i i~~~i i i r i i r i T~ i i r
7 8 9 10 11 12 13 14 15 16 17 IB 19 20 21 22 23 24
Hours (GMT)
SOURCE + Mobile H Area 0 Stationary O Total
Figure 3. Hourly VaciaLion of' VOC Emissions for ;i Summer Weekday
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—-A A A
a—a—H—B-H—
3—H—• H—H-
i i i i i
1 2 3 A 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23
Hours (GMT)
SOURCE + Mobile U Area 0 Stationary O Total
Figure A. Hourly Variations of NQX Emissions for a Summer Workday
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10 11 12 13 14 15 16 17 18 19 20 21 22 23 24
Hours (GMT)
SOURCE 4- Mobile H Area 0 Stationary O Total
Figure 5. Hourly Variation of CO Emissions for a Summer Weekday
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SECTION 3
EVOLUTION OF THE ROMNET BASE YEAR INVENTORY
PARENT EMISSIONS INVENTORIES
The ROMNET base year inventory is derived from che 1985 emissions data
base for the National Acid Precipitation Assessment Program (NAPA?), which in
turn is derived from the National Emissions Data System (NEDS). Some
modifications to the NAPA? data were necessary because of inherent differences
between ozone modeling and acid rain modeling, but the NAPA? data base
provides a number of benefits as a starting point for ROMNET. Chief among
these benefits is the extensive data gathering and quality control effort that
went into the NAPAP data base. The NAPAP data base also provides a consistent
inventory for the entire ROMNET domain, including the Canadian section.
Finally, data management software developed under NAPAP allows the flexibility
to make the adjustments needed for ozone modeling, including VOC speciation
and temperature adjustments.
The 1985 NAPAP emissions data base covers the 48 contiguous United
States, the District of Columbia, and Canada to 60° north latitude. Emissions
data are included for VOC, THC, CO, S02, NOX, NO, N02, four other acid gases,
32 hydrocarbon classes, and 15 classes of particulate matter. The overall
data base includes two basic inventory -types: an annual inventory, and a set
of 12 temporal scenario inventories representing the typical weekday, Saturday
and Sunday in each of the four seasons.
As noted above, the 1985 NAPAP inventory is derived in to a large extent
from EPA's National Emissions Data System (NEDS). NEDS inventories have been
compiled on an on-going basis by EPA's National Air Data Branch from data
submitted by State Agencies. For the 1985 inventory, NAPAP added to che
existing quality control process tor Siace ^ZZ.5 submitcalo and provided
assistance to State Agencies in addressing problems pointed out by the quality
control checks. The final 1985 NEDS inventory was then used as che basis for
the annual 1985 NAPAP inventory. Both the 1985 NEDS inventory and the 1985
NAPAP annual inventory are products of the cooperative efforts of EPA, State
environmental agencies, and Environment Canada. The NAPAP temporal scenario
11
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inventories were generated from the NAPAP annual inventories using emissions
allocation methodologies described below.
NAPA? EMISSIONS ALLOCATION METHODOLOGIES
In addition to the NAPAP data base, the ROMNET inventory development
effort has relied heavily on associated data management software developed
under NAPAP. This software, known as the Flexible Regional Emissions Data
System (FREDS), is used to prepare a gridded hourly data base suitable for
input to atmospheric models. FREDS consists of several independent modules,
some of which are written in Statistical Analysis System (SAS) command
language while others are written in FORTRAN. Figure 6 summarizes the modules
used in FREDS and the input data required by these modules. The following
discussion gives an overview of FREDS and its inputs as background to
i
additional methodologies developed under ROMNET. Additional detail on FREDS
and on the various allocation factors can be found in documents prepared under
NAPAP.2'3'4
The initial annual inventory has only one field for organic compound
emissions, in which either VOC or THC is entered, depending on the source
category. The Hydrocarbon Preprocessor uses methane emission data to
calculate emissions of the missing pollutant, so that the output from this
step contains both THC and VOC emissions. Other non-reactive pollutants are
treated as VOC in this step. For some source categories, the Hydrocarbon
Preprocessor adjusts THC and VOC to add formaldehyde, which is not detected by
some hydrocarbon measurement techniques.
The annual inventory also contains data on a number of pollutants besides
VOC, THC, NOX, and CO. Entries for these other pollutants are removed in the
Model Data Extraction step, in order to reduce computer processing time.
The Speciation Module divides THC and VOC into reactivity classes, and
NOX into NO and N02, using speciation factor files compiled by the PSPLIT
program. The Spatial Allocation Module assigns emissions to modeling grids,
and the Temporal Allocation Module resolves annual emission rates into hourly
rates for different seasons and day-types. The order in which these three
modules are run depends on the inventory subset being processed. For mobile
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Input Data
FREDS Modules
Annual
Inventory
Aldehyde
Factors
Species
Profiles
Spatial
Allocation
Factors
Temporal
Allocation
Factors
—
\
^
PSPLIT
*
/
\
s*
^
—
\
/
Hydrocarbon
Preprocessing
\
/
Model Data
Extraction
\
/
Speciation
\
/
Spatial
Allocation
\
/
Temporal
Allocation
\
/
Model Input
Preprocessor
Figure 6. Summary of Software Modules and Input Data Used in FREDS
and area source inventories, the modules are run in the above order. For
point sources, spatial allocation is performed first, followed by temporal
allocation and speciation. The last module of FREDS is the Model Input
Preprocessor, which produces a final rosolved inver.tcrv in SAS and EBCDIC
format suitable for use in atmospheric modeling.
For point sources, spatial allocation to modeling grids is based on
point-specific UTM coordinates in the NEDS inventory. Temporal allocation for
13
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point sources is based raainiv on operating data provided in the inventory.
State- and category-specific operating profiies were developed for certain
utility groups based on data provided by the Department of Energy and the
Tennessee Valley Authority. Soeciation factors for point sources as well as
area and mobile sources are source category averages based on average emission
composition.
Spatial and temporal allocation for area and mobile sources are
necessarily based on average factors, since these sources are handled as
county and source category aggregates in the parent annual inventory. Spatial
allocation factors are based on land use patterns, population distributions,
and spatial distributions of other emission surrogates and thus are specific
to counties and source categories.
METHODOLOGIES DEVELOPED AND MODIFICATIONS MADE UNDER ROMNET
«\
A number of modifications were made to the 1985 NAPAP data base and data
management software to meet the specific requirements of the ROM modeling
effort. These modifications involved: (1) VOC reactivity classifications,
(2) additional quality control checks, and (3) adjustments for temperature and
other weather conditions.
VOC reactivity classes used in ROM differ from those used in the Regional
Acid Deposition Model (RADM) for NAPAP. In ROMNET, VOC emissions were
classified into the Carbon Bond IV reactivity groups used in ROM. Second,
quality control checks were conducted under ROMNET for major sources of CO
emissions and for VOC emissions from hazardous waste treatment, storage and
disposal facilities (TSDF).
The main ROMNET modifications to NAPAP and NEDS emissions involve the
variability of emissions from some source categories with temperature and
other weather conditions. This variability is especially important for
evaporative VOC emissions from mobile sources, but weather conditions also
affect VOC emissions from other categories as well as NO. and CO from mobile
sources. The NAPAP data base gives emissions on a typical summer day, while
ROMNET will be used to model ozone episodes, or periods when ozone
concentrations are elevated in the ROMNET region. Ozone episodes are
14
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characterized by hoc weather, even for summer, with no storm systems over the
region.
Temperature corrections were made for major emission sources that are
particularly temperature-sensitive. In most cases, a single adjustment was
made to reflect the temperature and conditions on a typical ozone exceedence
day. Fcr mobile sources, though, evaporative gasoline emissions are very
sensitive to changes in daily temperature, especially at temperatures above
75°F. Therefore, 'the base year inventory for mobile sources includes
sufficient information to make emission adjustments for daily temperatures at
the grid level. Along with the temperature corrections for mobile sources,
adjustments were also made to reflect the latest changes to EPA's MOBILE
emission factor model. All of the modifications to the NAPAP inventory made
for ROMNET will be discussed in detail in subsequent sections.
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SECTION 4
SPECIATION OF VOC TO CARBON BOND IV REACTIVITY CLASSES
Figure 7 illustrates the VOC speciation process implemented in the PS?LIn
program and the Speciation Module of FREDS. PSPLIT requires three input
files. The first file gives a set of detailed "species profiles" for major
source categories. Emissions of individual species are given in terms of
weight percent for each source category profiled.. VOC profiles are available
for over 300 major source categories covering over 600 indivicua^ organic
compounds.
"Species Profiles"
(VOC Compositions
for Major Source
Categories)
Assignments
of SCC
Co Species
Profiles
\/
PSPLIT
I
Speciation Factors
by SCC (Moles of
each CB-IV Class
per ton VOC)
V
FREDS
Speciacion
Module
Assignments of
Specific Compounds
to Carbon Bond IV
Reactivity Classes
V
Figure 7. VOC Speciation Methodology
16
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The second input file indicates which species profile should be used for
each NEDS point Source Classificacion Code (SCC) or area source cacsgcjy ..Gue.
The third PSPLIT input file specifies the grouping of the over 600 individual
organic compounds into reactivity classes. Data in these three files are
processed in PSPLIT to produce a single output file, which is input to the
FREDS speciation module. The PSPLIT output file contains a sGp~ra~e record
for each NEDS SCC (point) and area source category code, specifying the
allocation of VOC emissions among L-eactivity classes in units of nicL = 5 o&: ccr
of VOC.
The need for a separate speciacion effort for ROMNET arises from
differences between the Carbon Bond IV (CB-IV) classification used in ROM for
VOC reactivity, and the RADM modeling classification system used in NAPAP.
These differences require replacement of the third PSPLIT input file, which
assigns individual compounds to reactivity classes.
The Carbon Bond IV (CB-IV) system, developed by System Applications Inc.
(SAI), assigns species to classes on the basis of carbon bond structures.
Because a single compound can contain different structures, a species can be
apportioned to more than one class. Eleven carbon bond classes are used in
ROMNET: olefin (OLE), paraffin (PAR), toluene (TOL), xylene (XYL),
formaldehyde (FORM), other aldehydes (ALD2), ethylene (ETH), isoprene (iJO),
nonreactive (NR), methane (METH), and methanol (MTHL). Five of these classes,
formaldehyde, ethylene, isoprene, methane, and methanol, are reserved for the
compounds for which they are named. The other six classes represent
structural groups.
A partial list of species and their CB-IV assignments is given in
Table 2, along with a key to the use of CB-IV classes. Appendix 3 gives a
complete list of CB-IV assignments for all of the compounds appearing in the
ROMNET inventory. Each entry in the CB-IV class matrix refers to the number
of structures of a certain cype LLI che given compound. For e::_:::r_-, 1,'_ , I , ^
tetramethylbenzene (SAROAD Code 45237) has been classified as one XYL and two
PAR, where XYL refers to a xylene structure and PAR refers to a saturacea
carbon atom. The reactivity class assignments in Table 2 and Appendix B were
made by SAI.
-------
TABLE 2. PARTIAL LIST OF CARBON BOND IV ASSIGNMENTS
OLE
PAR TOL XYL FORM ALD2 ETHY I30P
NR METH MTHL
43105
43106
43107
43108
43109
43110
43111
43112
43113
43114
43115
43116
43117
43118
43119
43120
43121
43122
43123
43124
Isomers of Hexane
Isomecs of HepCane
Isomers of OcCane
Isomers of Nonane
Isomers of Decane
Isomers of Undecane
Isomers of Dodecane
Isomers of Tridecane
Isomers of Tetradecane
Isomers of Pencadecane
C-7 Cycloparaffins
C-8 Cycloparaffins
C-9 Cycloparaffins
Mineral Spirics
Laccol Spirics
Isomers of BuCene 1.0
Isomers of PenCene 1.0
Isomers of PenCane
Terpenes 1.0
C9 Olefins 1.0
6.0
7.0
8.0
9.0
10.0
11.0
12.0
13.0
14.0
15.0
7.0
8.0
9.0
6.0 1.0
8.0
2.0 ^
3.0
5.0
8.0
7.0
CARBON BOND IV CLASS DESCRIPTIONS:
OLE -- Olefin group, two carbons connected by a double bond
PAR -- Paraffinic, or saturated, carbon group (one carbon ~-ith associated hydrogens)
TOL -- Toluene group
XYL -- Xylene group
FORM -- Formaldehyde molecule
ALD2 -- Other aldehyde group, -(HC-0)
ETHL -- Ethylene molecule
ISOP -- Isoprene molecule
NR -- Nonreactive carbon (one carbon with associated hydrogen, chlorine, etc.)
METH - - Methane molecule
MTHL -- Methanol molecule
13
-------
C3-IV is much more complex than the RADM classification system, where
each compound is assigned to a single reactivity class, and In face the two
systems are implemented in different versions of the PSPLIT program. A Carbon
Bond version of PSPLIT had been developed for earlier ozone modeling studies,
but this version required some enhancements to process the ROMNET inventory.
The earlier Carbon Bond PSPLIT was designed to handle far fewer "species
profiles" and individual compounds than are used in the 1985 NAPAP and ROMNET
inventories.
The following enhancements were made to the Carbon Bond version of PSPLIT
for the ROMNET inventory: the maximum number of species profiles was
increased from 175 to 320; the maximum number of species per profile from 75
to 325; the maximum overall number of species was increased from 500 to 641;
the maximum number of records in the species profile file was increased from
2000 to 4500; and the maximum number of SCCs was increased from 1400 to 4000.
19
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SECTION 5
QUALITY CONTROL
QUALITY CONTROL OF THE PARENT NAPAP INVENTORY
The NAPAP quality control effort was designed to meet three major
requirements of the modeling community. One requirement is self-evident:
that the data base be complete and of the highest possible quality. A second
requirement was that the emission estimation methods and the data base
timeframe be consistent across State boundaries, with emissions data
reflecting 1985 operating conditions as closely as possible. The third
objective was to provide an audit trail system for tracking problems or
potential errors. The NAPAP quality control effort addressed all of the
components of the inventory, including: annual emissions data for point, area
and mobile sources; temporal, spatial, and species allocation factors; and the
emissions allocation software (FREDS and PSPLIT),2-4
For point sources, plant records were screened by computer to identify
invalid or missing State, county, Air Quality Control Region (AQCR), plant, or
point identifiers. Another screening check highlighted missing and
inconsistent emissions and operating data as well as data that fell outside
normal ranges. The inventory was also checked for completeness to ensure that
all major point sources were included. Plants reported in the inventory were
checked against lists of plants from independent sources such as trade
association publications, industrial directories, and other EPA plant lists.
A major objective of'the quality control effort was to. stimulate review
of the data by State Agency personnel, who are most familiar with emissions in
their States. Results of the completeness checks and any discrepancies
pointed out in the screening checks were forwarded to appropriate State
agencies for correction or confirmation of the quescionabia encries. 3c=ices
also reviewed area and mobile source emissions estimates.
A similar process was used for the Canadian component of the NAPAP
inventory. Emissions data submitted by Environment Canada were checked for
compatibility with the FREDS system and for consistency with U.S. emissions.
20
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Questions were forwarded to Environment Canada and corrections mads fay the
Canadians were incorporated into the final inventory.
QUALITY CONTROL EFFORTS UNDER ROMNET
Additional quality control was conducted under ROMNET for CO emissions
from major point sources and for VOC emissions from hazardous waste treatment,
storage, and disposal facilities. Errors identified in these chectcs were
corrected in the ROMNET inventory as well as the parent NAPAP inventory. In
addition, the ROMNET inventory was compared with the parent NAPAP inventory in
different stages of its development in order to ensure that development was
proceeding as expected.
Major Point Sources of CO
v
The NAPAP quality control effort focused on S02, NOX, and VOC emissions,
because these are the major precursors in acid deposition processes as modeled
by the Regional Acid Deposition Model. Quality control checks for point
sources of CO and particulate matter were performed as resources permitted,
but these checks did not receive a high priority. Because CO is more actively
involved in the ozone-forming reactions modeled in the Regional Oxidant Model,
additional quality control of CO emissions was performed in ROMNET.
Highway mobile sources are the major source of CO emissions, accounting
for about 73 percent of the total for the ROMNET region. Other area sources,
mainly non-highway mobile sources and area source combustion categories,
account for about 17 percent, and point sources account for the remaining
10 percent. Most major sources of CO emissions are also major sources of at
least one of the NAPAP priority pollutants (S02, NOX, or VOC). Therefore, the
NAPAP quality control effort:, although focusing on NA?A? priority pollutants,
also addressed CO to a large extent for these categories. This is especially
true of mobile sources and area source combustion categories. On analysis of
the NAPAP quality control procedures for these categories, no further quality
control was judged to be necessary for CO area and mobile sources, despite
their large contributions to total CO emissions.
-------
rurzher. the NAPAP comD.le~er.ess cnecks, designed. to identify manor point
sources cnac were noc inciuaea in the iN'EDS invencory, were decermined adequate
for CO. Thus, the only additional quality control needs identified for CO
vera checks for pc=3ible calculation, coding, and transcription errors in the
point source inventory. Such errors would be minor in comparison with CO
emissions -~rom the -.OMNET resion or from anv given State, but might have a
significant imuact on emissions in specific grid cells.
Computerized screening jhecf.s vere mads on poir.- sources with reported CO
emissions o£ over 1000 tons in 1985. The checks focused on four conditions
which might indicate errors in reported emissions:
1. Reported emissions were based on an emission factor (Estimation
Method 3 or 5), but substantially exceeded (by more than a factor of
i) emissions that vouid have been calculated using EPA emission
factors.
2. Reported throughput was higher*than reported maximum hourly rate.
3. Reported emissions were very high in comparison with other sources
with the same Source Classification Code (SCC) .
4. An emission factor was used to calculate emissions but no throughput
was reported.
These criteria ao not necessarily indicate errors in emissions, but point out
inconsistencies within the NEDS data for a given source, inconsistencies
between tne 'TEDS data and standard EPA emission factors, and emissions that
fall outside normal ranges.
The NEDS inventory for the ROMNET region was screened, and sources
meeting any of the above criteria were flagged. Pertinent data were tabulated
for the flagged sources, and State ROMNET representatives were asked to review
the tables and either verify the reported data or make appropriate
corrections. A total of 44 changes were made by the States and incorporated
j.nco cne rcGiiNE-T as wej.i as cne parent o<>.r^.r inventory. whenever possioie, che
changes were also incorporated into the NEDS inventory. Two changes from West
Virginia were received after the final 1985 MEDS update, and consequently were
only made in the ROMNET and ^TAPAP ir.ventoriss. Appendix C lists changes mads
to the inventory as a result of the CO quality control effort.
-------
VOC Emissions from Hazardous Waste Treatment:. Storage and Disposal Facilities
When VOC emissions in the ROMNET region were first summarized by State
and emission category {as in Tabla 1). ths contributions of hazardous waste
treatment, storage, and disposal facilities (TSDF) for some States,
specifically Ma.Lne and West Virsinia. were unusuallv large. Therefore a
quality control effort was initiated ur.der ROMNET to detect possible errors in
cne TSDF emissions estimates. TS'DF v'OC estimates in NAPAP originally were
ootained from EPA's Emission Standards Division (ESD) which is undertaking an
emissions assessment of the category. Some processing of the ESD data had
been done under NAPAP to produce county-level emissions estimates suitable for
the area source inventory.
In the ROMNET quality control effort, intermediate results from the NAPAP
processing stsps were checked against results obtained in a previous,
t
independent analysis of the ESD data conducted by SAI. A number of
discrepancies were identified between the two data sets, including major
discrepancies in West Virginia and Maine. However, the models and data that
ESD uses to estimate TSDF emissions have not been finalized and are updated
frequently. In fact, the NAPAP and SAI data sets had been developed from
different versions of the ESD data, and on consultation with ESD the
discrepancies were found to have arisen from changes in the ESD TSDF emissions
data base -.hat were made between these two versions. The NAPAP and SAI
analyses had both been correct although they yielded different results in a
number of cases. Further, ESD indicated that additional changes have been
made since the NAPAP and SAI analyses.
Due to time and resource constraints, it was not possible to regenerate
TSDF emissions estimates using the latest ESD data. Instead, the NAPAP data
set was compared with the latest ESD data only for those specific entries
•vnere uiscrepancics nau appeared, oecween cne iNAJrAP and SAI analyses. This
comparison indicated that the NAPAP inventory was close to the current ESD
daca in most cases, but that changes were auoropriate for one countv in West
Virginia and one county in Maine. The following changes were made to both the
ROMNET inventory and the parent NAPAP inventory:
o annual VOC emissions from York County, Maine, TSDFs (originally
57,709 tons) were multiplied by a factor of 0.0012753
-------
o annual VOC emissions from Putnam County, west Virginia, TSDFs
(originally 139,467 tons) were multiplied by a factor of 0.4156
In addition, emission estimation methodologies for TSDF and area source
solvent evaporation were studied under R.OMNET to identify potential double
counting of VOC emissions in chese categories. Area source solvent
evaporation emissions are estimated by nass balance from nationwide solvent
sales. The emissions are ~hen allocated to States, counties, and various
source types (i.e. drycleaning, degreasing, etc.) based on employment data for
the solvent using industries, and population data (for architectural coatings
and miscellaneous non-industrial solvents). Solvent emissions reported in the
point source inventory are subtracted in these calculations, and another
13 percent deduction is mace from industrial surface coating categories to
account for emission controls.
Because TSDF emissions also include^evaporation of waste solvents, the
possibility of double counting exists. In fact, waste solvents may account
for as much as 50 percent of TSDF emissions. For the ROMNET domain,
50 percent of TSDF emissions amounts to about 330 tons of VOC per day
(unadjusted for temperature). For comparison, the total area source solvent
emission rate for the ROMNET domain is about 6200 tons per day (unadjusted).
The 18 percent control assumption for industrial surface coating may
offset a good portion, if not all, of the potential double counting error.
Emission controls used at plants in the area source category generally are not
destructive, in that the captured solvent is reused and ultimately drummed and
sent to a TSDF or other disposal facility. Eighteen percent of industrial
surface coating in the ROMNET area source inventory corresponds to about
370 tons per day, which is greater than the solvent portion of TSDF emissions
in the region.
Information is not available on the extent to which destructive controls
are employed by solvent users in the area source inventory, or on the extent
to which solvents are shipped to disposal facilities other than TSDFs.
Therefore, no conclusions can be drawn ac this time whether TSDF emissions and
solvent emissions in the ROMNET domain overlap, or on the potential magnitude
of any double counting error. However, because of the emission control
-------
deduction in the soivenc balance, che potential error would appear to be
minimal.
Comparison of ROMNET and NAPA? Emissions
Because of the number Df steps used in FREDS, data processing errors are
possible in the preparation of the final modelers' inventories. In order to
detect and correct such errors, various checks were made as the preparation of
the ROMNET inventory progressed. These checks involved comparison of the
ROMNET inventory with the NAPA? inventory for the ROMNET region after each
FREDS processing step. Any discrepancies were investigated and corrected.
The final ROMNET annual inventory is consistent with the 1985 NAPAP version
2.0 inventory.
25
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SECTION 6
MOBILE SOURCE ADJUSTMENT
The purpose of mobile source adjustment in ROMNET was to produce
emissions estimates that reflect EPA's latest revisions to the MOBILE emission
factor model, and that ara representative of the high temperatures during
ozone episodes. In addition, emission'estimates in the mobile inventory are
revised to reflect differences between initial control efficiency estimates
for motor vehicle inspection and maintenance (I/M) programs, and revised
efficiency estimates'.
MOBILE is an empirical model used by EPA to calculate emissions from
mobile sources under different conditions. Maintained by EPA's Office of
Mobile Sources (QMS), ic calculates emission factors on a gram per mile basis
for different types of vehicles at different speeds. These emission factors
depend on average daily temperature, diurnal temperature variation, and other
model inputs such as vehicle age distribution and operating conditions.
Emission factor calculation algorithms in MOBILE recently were revised and at
present are undergoing additional revisions to incorporate new test data.
These revisions primarily affect calculations of VOC emission factors for fuel
evaporacion.
Emission rates in the parent inventories were generated with MOBILE 3.0
using annual average ambient temperatures at the State level. MOBILE 3.O., the
most current publicly-released MOBILE version at this writing, includes
temperature-dependence functions for exhaust emission factors, but not for
evaporative VOC. MOBILE 3.9, the current EPA. in-house version, relates
evaporative emission factors to average ambient air temperature, diurnal
temperature variation and fuel volatility expressed in terms of Reid vapor
pressure (RVP). A MOBILE 4 model, released afcer completion of chis
invencory, adds calculations for running LJSG and excess evaporation bas^d -n
recent test data. Both of these terms refer to evaporative emissions caused
by the inabilitv of existing carbon adsorption fuel vapor control systems to
handle recent increases in fuel volatility. Running losses occur while the
vehicle is running and excess evaporation occurs while the vehicle is
standing.
-------
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30
•Id
-------
Figures 3 and 9 show Che impacts of average daily temperature and diurnal
temperature variation, respectively, on VOC emission factors predicted by
MOBILE 3.0 and MOBILE 3.9. The figures also illustrate the estimated
additional contribution of running loss and excess evaporation to total VOC as
calculated using algorithms provided by OMS which are described later in this
section. NO., and CO emissions also vary with average ambient temperature,
although to a lesser extent than VOC. These pollutants are not affected by
the range in diurnal temperature changes.
As Figure 8 shows, the effect of average daily temperature on VOC
emissions is minimal up to about 70°F but is substantial at the higher
temperatures representative of ozone episodes. Because of this strong
dependence on temperature, and because the mobile source inventory accounts
for a substantial portion of the overall inventory, the mobile methodology was
designed to allow grid-specific adjustments based on average temperature and
\
diurnal variation for each ozone episode day that is modeled.
ADJUSTMENT METHODOLOGY
Development of the mobile adjustment methodology was complicated by the '
volume of data that goes into the mobile source inventory. There are twelve
categories of highway mobile sources for each county in the NEDS inventory,
made up of a matrix of four vehicle types by three roadway types. The vehicle
types included in the inventory are light duty gasoline vehicles, light-duty
gasoline trucks, heavy-duty gasoline vehicles, and heavy-duty diesel vehicles.
The roadway types are limited-access highways (50 miles per hour), rural roads
(45 mph), and urban roads (19.6 mph). Each combination of vehicle type and
road type is derived from a separate MOBILE 3.0 emission factor and is entered
separately in the NEDS inventory.
Day- and grid-specific ceraperature acjuscmenc on a. cacegoi/y-oy-oaccgory
basis would have required production of a set of 'gridded, hourly inventories
for each of the twelve mobile source categories. On the other hand, lumping
the twelve categories together prior to the adjustment would not allow
county-level variations in vehicle- and road-type distributions to be
reflected in the adjustment factors, causing errors in the county- and grid-
29
-------
level emissions. The general goal in developing a methodology was to limit
daca processing requiremencs for the adjustment, while minimizing the errors
introduced by any simplifying assumptions.
Other factors also complicated the design of an adjustment methodology.
For example, the use of mobile source inspection and maintenance (I/M)
programs varies across the region, and the effectiveness of these programs in
reducing emissions has been shown to vary widely from State to State. In
addition, evaporative emission factors, exhaust emission factors for gasoline
vehicles, and diesel exhaust emission factors respond differently to
temperature and have significantly different ;70C species compositions. Thus,
the distribution of VOC across reactivity classes varies with temperature.
The final methodology adopted for ROMNET involves a two-step approach
which satisfies all of the above goals. The basic approach is to make most of
the necessary adjustments on a category-specific basis with the annual mobile
inventory. A detailed adjustment is still possible for the annual inventory
because that inventory is not yet resolved into hourly emissions by reactivity
classes and grids. The resulting interim inventory is then gridded and
temporally allocated and the twelve vehicle and road classes are consolidated.
In the second step, the gridded hourly inventory is fine tuned for
modeling applications with day- and grid-specific temperature adjustments.
With the two-step approach, adjustment errors are minimized without a large
increase in the overall data processing requirement. The selected methodology
also takes into account differences in I/M efficiency across the region, and
the dependence of VOC speciation on temperature.
In the first step, each category of the annual mobile inventory is
adjusted separately co reflect MOBILE 1-. '-? -.micsion factors and to add rur.nir.^
loss and excess evaporation. Also, the temperature basis of the inventory is
changed from the State-specific annual averages used in NEDS (ranging from
about 45°F to 58°F for the ROMNET region) to a common region-wide daily
temperature and diurnal variation. Although temperature is never expected to
be constant across the entire region, this temperature leveling greatly
30
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simplifies both steps of the adjustment process. A daily average of 35°? and
a diurnal variation of 20°F were selected as the common region-wide
temperature parameters. These values yield the median emission factor for the
range of temperatures expected over the ROMNET region in an ozone episode
(about 70°F to 90°F) .
The basic approach is to divide each entry in the mobile source inventory
by the MOBILE 3.0 emission factor used to produce it originally, and then co
multiply by a new emission factor. Both factors are specific to the cvelve
vehicle and road classes. The MOBILE 3.0 emission factors vary from j-cace to
State to account for the State -Level annual average temperatures used in the
parent inventory. The new emission factors reflect the common region- wide
temperature parameters: an 85°F average temperature, and a 20°F diurnal
variation. For CO and N0x, the new emission factors are simply MOBILE 3.9
emission factors, while the new VOC factors include MOBILE 3.9 predictions as
well as terms for running loss and excess evaporation. The above operation
amounts to multiplying emissions in the parent inventory by a ratio of
emission factors to give new emissions estimates that reflect changes in
MOBILE and are representative of the selected 85°F temperature.
The general algorithm for Step 1 can be summarized by the following
equation used for N0x:
INTNOX(Xvs = NOXERS * (EFNOX3 .
where: INTNOX = interim NOX emission rate ( tons /year ),
NOXER3 = NOX emission rate in NEDS (tons/year),
EFNOX3.9= uncontrolled MOBILE 3.9 NOX emission factor (g/mile) , and
EFNOX3 = controlled MOBILE 3.0 NOX emission factor (g/mile);
subscripts: o refers to the common temperature conditions for adjustment
(85°F average and 20°F diurnal variation) ,
a refers to State annual average temperatures used in NEDS,
o refers to cour.cy,
s refers to a road type, and
v refers to a vehicle class .
31
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I/M control efficiency assumptions used in the NEDS inventory are removed
in Step 1 by using a controlled MOBILE 3.0 emission factor and an uncontrolled
MOBILE 3.9 emission factor. This results in a leveling of control assumptions
in the intermediate inventory, which greatly simplifies future analysis of
mobile source control strategies. The original I/M assumptions are also
replaced by revised efficiency estimates in Step 2.
For VOC emissions, Step 1 is somewhat more complex for two reasons. The
first is the addition of running loss and excess evaporation to the final
MOBILE 3.9 emission factor. The second complicating factor is the need to
account for changes in VOC speciation as the mix of evaporative, gasoline
exhaust, and diesel exhaust emissions changes with temperature. All
evaporative emissions are associated with gasoline vehicles; diesel
evaporation is believed to be negligible.
To accomplish this, the numerator in the VOC emission factor adjustment
is divided into separate terms for exhaust and evaporative, with the
evaporative term covering running losses, excess evaporation, and evaporation
predicted by MOBILE 3.9. In addition, gasoline exhaust emissions are compiled
separately from diesel exhaust emissions. Thus, VOC emissions in the interim
file are separated into evaporative emissions, gasoline exhaust, and diesel
exhaust, making possible a temperature-specific calculation of species
breakdowns in the second adjustment step.
Step 1 for VOC is illustrated by the following set of equations:
EFEVAP^ = EFS.g^ + EFRUN^ + EFEXC^
^^ VOCER3 * (EFEVAP YEFVOC3 ^
0095 scgs ogs' sgs
VOCERS.^ * (EFEXHG^/EFVOCS^)
VOCER3acds * (EFDIES^/EFVOCS^)
where: EFEVAP = total new emission factor for evaporative VOC (g/mile),
EF3.9 = MOBILE 3.9 evaporative VOC emission factor (g/mile),
EFRUN = running loss amissic- factor (g/r.ile) .
EFEXC = excess evaporative emission factor (g/mile) ,
INTEVAP = interim evaporative emission rate (tons/year),
-------
VOCER3 = NEDS VOC emission rate based on MOBILES (tons/year),
EFVOC3 = controlled emission factor used to develop NEDS estimate
(g/mile),
INTEXHG = interim emission rate (uncontrolled) for exhaust from
gasoline vehicles (tons/year),
EFEXKG = uncontrolled MOBILE 3.9 emission factor for gasoline
exhaust (g/mile),
INTDIE3 = interim emission rate (uncontrolled) for exhaust from
diesels (tons/year), and
EFDIES = uncontrolled MOBILE 3.9 emission factor for diesel exhaust
(g/mile);
subscripts: o,a,c,s are the same as for NOX (above),
g refers to a gasoline vehicle type, and
d refers to diesel vehrcles,
Following Step 1, mobile source emissions are aggregated to county
totals, retaining separate totals for the evaporative emissions, gasoline
exhaust, and diesel exhaust. The resulting interim mobile inventory is then
processed through FREDS to produce gridded, speciated, hourly inventories for
the three summer day-types (weekday, Saturday, and Sunday). These inventories
are processed in Step 2 of the adjustment process.
Step 2
Step 2 fine tunes the mobile emission estimates at the grid level to .
reflect observed temperatures on the episode days being modeled. This step is
performed using a table of mobile source emission factors for different daily
average temperatures and diurnal ranges. The table (given in Appendix D)
covers average daily temperatures ranging from 40°F to 90°F and diurnal
variations of 0°F to 40°F. Because vehicle and road classes in the original
inventory are grouped together at Stsc 2, the final adlustment table ~or.ra.ir.s
"composite" emission factors, or weighted averages of factors for the various
classes which represent typical distributions in vehicle and road types over
the ROMNET region. However, VOC emission factors are divided into
. 33
-------
evaporative, gasoline exhaust, and ciiesel exhaust components to allow
recalculation of VOC species breakdowns based on final grid- and day-specific
temperatures. The evaporacive VOC factor includes evaporation calculated by
MOBILE 3.9, running loss, and excess evaporation.
Step 2 is implemented as an input step to the Regional Oxidant Model by
EPA's Atmospheric Research and Exposure Assessment Laboratory (AREAL) and is
carried out separately for each day being modeled. Emission factors are
looked up in the Step 2 adjustment table using the daily average temperature
and diurnal range for each grid. The factors are then applied to emission
entries in the inventory. At the same time, revised emission control
efficiencies are applied. Emission control efficiencies are sensitive to
temperature for some pollutants, but temperature dependence for this parameter
is expressed in an explicit equation instead of in a table.
Step 2 can be summarized as follows:
S
FINCP9* - INTCpc9* * (EFTAB^/EFTABp,) * CF^
CFra = (1 - C(t)ra/100)
where: FINC = final controlled emission estimate (composite of all vehicle
and road classes, kg/hr),
INTO = interim uncontrolled emission estimate (composite of all
vehicle and road classes, kg/hr),
EFTAB = emission factor from the Step 2 adjustment table (g/mile),
CF = gridded control factor, and
C(t.) = revised control efficiency in percent (weighted average of
efficiencies for the counties making up grid g, adjusted by an
explicit function of t for some pollutants),
subscripts: p refers to pollutant (CO, NOX> evaporative VOC, VOC in
gasoline exhaust, or VOC in diesel exhaust),
g refers to grid cell,
d refers to the day being modeled,
h refers to the hour of the day,
o refers to the common temperature conditions in the Step 1
adjustment (85°F average and 20°F diurnal variation),
34
-------
t refers to average daily cempera.cu.re in cell g on day d,
and
r refers Co diurnal CemperaCure change in cell g on day d.
After Che final adjuscmenc of VOC emissions, VOC species profiles are
recalculaCed for each grid and day. This is done by using three separate sees
of VOC speciation factors co calculate molar emissions by reactivity class for
the evaporative, gasoline exhaust, and diesel exhaust components of VOC.
Total moles of each reactivity class are then calculated by combining che
resulCs for the three VOC components. With this recalculation, the final
speciation is representative of grid- and day-specific temperatures.
The final result of Step 2 is a gridded hourly inventory for each day
modeled, in which the emissions and VOC speciation in each grid reflect the
day-specific temperatures in that grid. Generally, ten or more days will be
modeled for each ozone episode that is studied. The daily gridded inventories
will be strung together and input to the ROM model.
Benefits of the Two Step Approach
The main advantage of this two-step approach is that the bulk of the
adjustment, on the basis of percent change, is done in Step 1 with a detailed
vehicle and road class breakdown. The aggregate adjustment in Step 2 is only
a fine tuning step, thus errors due to aggregation are minimized. In a test
of the approach, errors in the adjustment due to aggregation were below 5
percent for all counties in the region but one. The magnitude of error
predicted for this county, located in West Virginia, was less than 60 tons per
year. These estimated errors meet the goal set by the ROMNET Emissions
Committee of limiting errors in county-level predictions to less than 5
percent or 100 tons, whichever is greater.
Another advantage of the two-step approach is that the product produced
in Step 1 will be a stand-alone emissions inventory, reflecting temperatures
typical of an ozone episode (daily average of 85°F .and diurnal variation of
20°F) and also reflecting upcoming changes to EPA's MOBILE model. This
inventory will be useful in itself, even without the day specific temperature
adjustment.
35
-------
INPUTS FOR THE ADJUSTMENT
MOBILE Model Runs
A3 discussed above, MOBILE ^.J ^u-s for Step I were mace with the State-
specific annual average temperatures -hat were used to develop the 1935 NEDS
inventory. Step 1 also calls i'or MC3 CL'Z J.J emission factors cnat .reflect -/LI
controls, however I, M was rarely required Jcace-wiue ir. j.93: . Thus, cvo sets
of MOBILE 3.0 runs were needed for each State to cover chose counties affsctec
by I/M programs and those without programs. State-specific I/M program
characteristics were used, with programs assumed to be consistent for all
affected counties within a given State. MOBILE 3.0 emission factors were
generated for ail vehicle and road classes coverea in cne NEDS inventory.
Average speeds used in the model for the different road types were the same as
those used in the NEDS inventory: 19.5 miles per hour for urban roads, 45 mph
for rural roads, and 50 mph for highways.
These same speed assumptions were used for MOBILE 3.9 runs for both
Steps 1 and 2. An average gasoline Reid vapor pressure (RVP) of 11.5 was
assumed for the 1985 oase year, oasec on the ASTM classification for the
ROMNET States. For Step 1, emission factors for the different vehicle and
road classes are used separately. For Step 2, however, composite emission
factors are needed that represent average emissions for the 12 NEDS classes."
These composites were developed by taking weighted averages of the emission
factors for individual vehicle and road classes. The weighting factors were
based on average distributions of vehicle miles traveled (VMT) among the
various vehicle and road types for the ROMNET region.
Standard MOBILE defaults were used for any parameters not discussed above
in boch the ;iCSHZ J.3 and :1C3ILZ 2.~ :~-r.- . Tl;=se raramec^rs L.icl^ds vehicle
age distribution, percentage of cold starts, and altitude. The original NEDS
emission estimates were made using ccuntv-specific vehicle age distributions.
Use of default age distributions in all che successive adjustments allows that
initial detail to be retained through the succeeding steps.
-------
Calculation of Running Loss and Excess Evaporation
Running loss and excess evaporation were calculated using data and
algorithms provided by EPA's Office of Mobile Sources. P.unning loss is a
function of temperature, RV?, and vehicle speed:
?.L = . i:.S/o; •- -,:p(.0.08,263*T - ). 71323*?.VP • If. 243)
where: ~.L = cur.nir.g loss -zraos/milc.1 ,
S = vehicle speed (miles/hour)
T = hourly temperature (°F), and
RVP = Reid Vapor Pressure (pounds per square inch).
This equation is based on hourly temperature; however, for compatibility with
MOBILE 3.9 emission factors ana with the Step 2 temperature adjustment table.
running loss estimates were required for various daily average temperatures
and diurnal variations.
To obtain these daily estimates, a typical diurnal temperature pattern
was developed based on analysis of meteorological data for the ROMNET region.
This general pattern was used to derive an hourly temperature profile for each
combination of average temperature and overall diurnal variation covered in
the adjustment table. Hourly emission rates were then calculated using the
above equation. Finally, dailv emissions were calculated bv averag;in2; the
- - O J
hourly rates, weighted by a typical diurnal traffic pattern.6
For each combination of daily average temperature and diurnal variation,
running loss was calculated for the three speeds analyzed in MOBILE 3.0 and
MOBILE 3.9 modeling: 19.6 mph, 45 mph, and 50 mph. Results for the three
speed classes were averaged together to give composite factors using the same
weighting factors as for MOBILE 3.9.
Zxcaso evaporation ^_ ^apenasnt on R!."? and independent or cemperacure.
For the base year 1985 RVP of 11.5, excess evaporation is 0.669 grams/mile for
light-duty gasoline vehicles, 1.063 g/mile for light duty gasoline trucks, and
2.310 g/mile for heavy duty gasoline vehicles.5
-------
In both Steps 1 and 2 of the mobile adjustment, running loss and excess
evaporation are added to the evaporative component of VOC . For iiius tracion
purposes, however, these emissions are listed separately in Appendix D.
Methods for Canadian Mobile Sources
There are some differences in format becween the Canadian and United
States mobile source invencories. First, che annual Canadian inventory gives
emission rates only to the Province level. There is no smaller geographical
unit corresponding to the county level. In addition, the Canadian annual
inventory breaks mobile source emissions into four vehicle categories, but
does not break emissions into road or speed classes. Neither of these
differences required substantial changes in the adjustment methodology for
mobile sources. MOBILE 3.0 emission factors for the Canadian portion of the
ROMNET domain were obtained from Environment Canada. MOBILE 3.9 emission
factors were the same as those used for the U.S. portion.
ANALYSIS AND REJECTION OF SPEED ADJUSTMENTS
As noted above, the NEDS inventory uses average speeds of 19.6 miles- per
hour, 45 mph, and 50 mph to represent urban roads, rural roads, and freeways.
These same average speeds have been retained in the ROMNET inventory, although
a potential adjustment of emissions to reflect new speed assumptions was
considered.
The ROMNET speed analysis .was prompted by an independent uncertainty
analysis of the NEDS/NAPAP mobile sourca inventory that cited vehicle speed
assumptions as a source of uncertainty.7 A particular concern was the
19.6 mile per hour average speed for urban roads. Everyday experience
least during rush hours. In addition, questions were raised on the assumption
of 45 and 50 mph speeds for some classes of rural roads and highways.
Because emissions per rails increase sharply below 19.6 miles per hour, an
overestimate in vehicle speed would appear to imply an underestimation of
emissions. However, any analysis of potential emission adjustments for speeds
38
-------
'must Cake into account the derivation of the NEDS/NAPAP mobile source
inventory. In NEDS/NAPAP, county-level emissions for each vehicle and speed
class were calculated by taking the product of vehicle miles traveled (VMT)
for the class, and the appropriate MOBILE 3.0 emission factor in grams per
mile. VMT measurements are obtained from State Transportation Departments
where possible. In the ROMNET region, Delaware, the District of Columbia.
Maryland, Massachusetts, Vermont, and West Virginia provided VMT on a county
basis.
Where measured VMT are not available, a NEDS default algorithm is used to
compute county-level VMT based on allocation of motor vehicle gasoline and
diesel fuel to counties. Gasoline and diesel fuel consumption is determined
on a State by State basis by the Federal Highway Administration (FHWA).8
Vehicle registration data from R. L Polk and Company are used to allocate
State-level fuel consumption to counties.
The resultant county fuel consumption estimates are multiplied by
national average miles per gallon for each vehicle type (light duty gasoline
vehicles, light duty trucks, heavy duty gasoline vehicles, and heavy duty
trucks) to obtain county-level VMT estimates. National average mile per
gallon figures were obtained by dividing total nationwide VMT by total fuel
consumption for each vehicle type. County level VMT estimates by venicle type
were further allocated to the three road speed classes using FHWA data.
Thus, highway vehicle emissions estimates ultimately are based on fuel
use instead of VMT wherever the NEDS default algorithm was used, as was done
in over half of the ROMNET states. If average speed is decreased from
19.6 mph to a lower value, emissions per mile increase but average gasoline
mileage decreases at the same time. Because gasoline sales are fixed, a
decrease in gasoline mileage results in a corresponding decrease in VMT, which
acts to offset the increase in emissions.
j.nj_.j cTjiecu is i.XxusC"c.C3c \ _• _^*^r2 ^.'^, >.TiL~ri jr.or.'To cne -.r.p^Lcz -^
average speed on emissions per mile and gasoline mileage. These curves are
also combined to show the effect of speed on emissions per fuel consumed.
Gasoline mileage data in Figure 10 are for 1975 model vehicles under cyclic
(stop-and-go) driving conditions.9 Although the mileage measurements are
39
-------
dated, the general mileage-speed relationship probably has noc changed
substantially.
As the figure shows, emissions per fuel consumed are almost constant to
20 mph and decline slowly above this speed. Therefore, the effect on
emissions of any new speed assumptions, with appropriate adjustments to NEDS
fuel-to-VMT calculations, would be small in comparison with the complexity of
the required adjustment. In addition, data on actual speeds in urban areas
are sparse, and recent data generally are noc available. Thus, the Emissions
Committee judged that speed adjustments were not warranted at this time.
Ongoing assessment of these issues under NAPAP auspices will be reviewed as
the ROMNET study progresses.
-------
I 1
ICMISSlONS/GALLON
Mil liACF.
"3
H"
TO
C
o
o
(A
in
H'
O
D
(A
"X!
ft
"J
C
ft
n
o
3
u
n
a.
n:
O
I I
0.9 -
0.7
0.6
0.5
0.4
0.3
0.2
0.1
EMISSIONS/ I
25
35
SPEED (inilea per hour)
-------
SECTION 7
AREA SOURCE ADJUSTMENTS
In the NAPAP seasonal allocation methodology, calculation of summer
emissions is based on seasonal "activity" patterns. "Activity" in this sense
is similar to a throughput for a point source. Thus, the NAPAP allocation
factors do not take into account increases in emissions due co higher summer
temperatures. In addicion, data are lacking on seasonal activity patterns for
a number of VOC area source categories; therefore emissions from these
categories are assumed in NAPAP to be uniform throughout the year.
In the ROMNET inventories, VOC emissions from six different area source
categories were adjusted for temperature and weather effects. Three
categories were adjusted for temperature effects on vapor pressure:
o Gasoline marketing (Category 54)
o Bulk gas terminals and plants (103)
o Hazardous waste treatment, storage, and disposal facilities (109)
Another three categories were adjusted for affects of weather on activity
.patterns:
o Gasoline vessels (Category 52)
o Architectural coating (82)
o Miscellaneous solvent use (95)
The adjustment for gasoline vessels accounts for weather effects on the use of
pleasure boats, which make up the bulk of this category. The adjustment for
miscellaneous solvent use accounts for weather effects on pesticide use.
For architectural surface coating, one might expect the main weather
influence to be the effect of temperature on evaDoration rate. However.
temperature effects on evaporation rate are small in comparison with the
uncertainty of hourly solvent usage profiles. Thus, the main weather effect
for this category is the effect of rain and cold weather on cne use or
external oil-based paint.
These six categories contribute a total of about 5 percent to the overall
VOC inventory for the ROMNET region. The maximum contribution for any single
-------
category is 2 percent, for gasoline marketing. Since none of the six
categories rivals mobile sources for VOC emissions, a day-specific adjustment
was judged to be unnecessary. Rather, emissions were adjusted to reflect
conditions on a typical episode day. The adjustments were accomplished by
changing the summer temporal allocation factors for these categories. Table 3
gives the revised summer allocation factors for the six adjusted categories.
In NAPAP, a summer allocation factor of 0.25, corresponding to no increase in
emission rate, was used for each of these categories.
TABLE 3. REVISED SUMMER ALLOCATION FACTORS FOR AREA SOURCE CATEGORIES
Miscel- ' Bulk gas Hazard-
Gasoline
vessels
(52)
Connecticut
Delaware
DC
Indiana
Kentucky
Maine
Maryland
Massachusetts
Michigan
New Hampshire
New Jersey
New York
North Carolina
Ohio
Pennsylvania
Rhode Island
Tennessee
Vermont
Virginia
West Virginia
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
\J
0
0
.425
.425
.375
.425
.425
.500
.425
.425
.500
.500
.425
.425
.325
.425
.425
.500
.325
.500
.325
.425
Gasoline
market-
ing
(54)
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
w
0
0
.385
.368
.363
.358
.310
.398
.365
.370
.430
.413
.378
.380
.353
.360
.360
.335
.345
. -+-_<
.345
.315
Arch^itec-
tural
coating
(82)
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
\J
0
0
.500
.425
.425
.425
.425
.600
.425
.500
.500
.600
.425
.500
.425
.425
.425
.500
.425
.600
.425
.425
laneous
solvent
use
(95)
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
.251
.266
.250
.264
.308
.254
.265
.252
.288
.257
.253
.262
.268
.283
.262
.251
.268
.308
.267
.262
terminals
and bulk
plants
(103)
0.
0.
0.
0.
0.
0.
0,
0,
0.
0,
0.
0,
0.
0,
0,
c.
0
c
0.
0
,398
.380
,380
,355
,315
.405
.378
.380
,445
.423
.393
.390
.368
.370
.370
.395
.360
. -f £. -/
.358
.323
ous
waste
TSDF
(109)
0.300
0.300
0.300
0.300
0.300
0.300
0.300
0.300
0.300
0.300
0.300
0.300
0.300
0.300
0.300
0.300
0.300
A •: r ^
w . ^ \J\J
0.300
0.300
The original allocation factor in the NAPAP inventory was 0.25 for all of
these categories, corresponding to no increase in emissions during summer.
-------
Adiustments were also considered for a number of point source categories
and other area source categories, including degreasing and other industrial
solvent use categories. However, these operations are conducted indoors in
controlled environments, and hence are not influenced by outside temperatures
or weather effects. Adjustments were also considered for point source
volatile organic liquid storage, because emissions from these categories are
sensitive to temperature in the same way as bulk gasoline terminals and bulk
plants. However, adjustments of point source emissions would have been much
more difficult than area sources, and the combined contribution from point
source storage categories was only about 0.4 percent of the overall VOC
inventory.
Summer allocation factors in Table 3 were calculated using three basic
approaches described in the following sections.
GASOLINE MARKETING AND BULK GAS TERMINALS* AND PLANTS
Emissions from gasoline marketing, bulk gas terminals and bulk plants in
the annual inventory are based on standard emission equations given in EPA's
Compilation of Emission Factors (AP-42).10 These equations express emissions
in terms of liquid temperature, vapor pressure, barometric pressure, and tank
characteristics. The two area source categories are each composed of a number
of emission sources which are treated separately in AP-42, such as breathing
losses, working losses, and fugitive emissions from liquid transfer.
To formulate the adjustment calculation for a given source in a given
State, the emission equation for the source was written using the average
ozone episode temperature in the State, and divided by the same equation using
the State annual average temperature. Typical episode temperatures were
calculated at the State level by averaging daily temperatures during ozone
cpiiodss in j_>u3, LJ&'+I j.9o5, and j.3o/ J5^6cc5'_i oy crio .FvCl !!•> c, i .ioGciing
Committee as candidates for ROM simulations. Barometric pressure and tank
characteristic terms cancel, giving:
SF, _ (Q 25x * f[vp'(T)] * F(T')
SF ~ (°'25) * F(T°)
where: SF' = revised summer allocation factor (dimensionless) ,
44
-------
(0.25) = initial NAPAP summer allocation factor (dimensionless) ,
vp ' = vapor pressure under ozone episode conditions (pounds per
square inch), a function of temperature,
T' = typical liquid temperature during an ozone episode (°F) ,
vp° = vapor pressure used in calculating the annual emission rate for
the source (pounds per square inch) ,
T° = liquid temperature used to calculate annual average emissions
f[ ] represents the vapor pressure function used in calculating
emissions for the source (from AP-42) , and
F( ) represents the temperature function used in calculating
emissions for the source (from AP-42) .
Revised allocation factors for all of the different sources in each category
are then averaged, weighted by their appmoximate emission contribution, to
give a revised allocation factor for the overall category.
The above calculation was carried out separately for each State in the
ROMNET region. For bulk gas storage and bulk plants, liquid temperatures
during ozone episodes were assumed to reflect summer average air temperatures
rather than the elevated temperatures that occur during an episode. Because
of the size of most storage tanks, at least five days are required for bulk
liquid temperature to equilibrate with air temperature. Thus, the bulk liquid
temperature will be lower than the air temperature for most of the duration of
a typical ozone episode.
Gasoline marketing includes breathing and working losses from underground
storage tanks at gas stations (Stage 1) and fugitive losses from refueling of
cars (Stage 2). Because of the small size of automobile gas tanks, liquid
temperature in these tanks follows air temperature more 'closely than in large
tanks. Thus, typical ozone episode temperatures were used in the above
equation for Stage 2.
GASOLINE VESSELS ARCHITECTURAL COATING AND MISCELLANEOUS SOLVENT USE
Emissions from these sources are affected by large differences in
activity between favorable days and unfavorable days. In EPA's State
-------
Implemencation Plan (SIP) inventory guidance, emissions are viewed as roughly
constant on favorable days and negligible on unfavorable days. ' Thus,
emissions can be viewed as either on or off depending on weather condicions.
In the ROMNET adjustment, emissions on favorable days were increased to
compensate unfavorable days, keeping annual emissions constant. Annual
emissions in the parent inventory are based on State-level annual fuel and
solvent consumptions.
Pleasure boats make up the bulk of gasoline vessel emissions. On the
other hand, miscellaneous solvent use includes a number of components, only
one of which, pesticide application, is weather dependent in a predictable
manner. Other components of miscellaneous solvent use include room
fresheners, deodorants, and other consumer products. Similarly, architectural
surface coating includes boch interior and exterior paint use, with only the
excerior component being weather dependent. The ROMNET adjustment takes into
account weather-independent fractions of these categories.
The calculation of revised summer allocation factors can be summarized as
follows:
SF' = [(0.25) * (1-Wf)] + [(0.25) * Wf * SW]
SW = (0.25) * 365/(365-U)
where: SF' = revised summer allocation factor for the overall category
(dimensionless),
SW = revised summer allocation factor for the weather-dependent
fraction (dimensionless),
(0.25) = initial NAPAP summer allocation factor (dimensionless),
Wf = fraction of emissions that is weather-dependent
(dimensionless),
365 = number of days in the year, and
U = number of unfavorable days.
This calculation was carried out for each State in the ROMNET region.
Criteria for identifying favorable and unfavorable days were based on EPA's
SIP inventory guidance where possible.11 Label instructions on external latex
-------
paint were also used. Ozone episode davs were assumed to be favorable for all
activities.
HAZARDOUS WASTE TREATMENT, STORAGE, AND DISPOSAL FACILITIES
TSDF VOC estimates in the annual inventorv, were obtained from EPA's
Emission Standards Division (ESD) which is undertaking an emissions assessment
of the category. The summer allocation factor for this category was derived
from results of an analysis of the ESD data conducted by EPA's Economic
Analysis Branch. Insufficient data were available to calculate State-specific
factors.
47
-------
REFERENCES
1. Gery, M., G. Whitten, and J. Killus. Development and Testing of the
CBM-IV for Urban and Regional Modeling. EPA-600/3-88-012, U.S.
Environmental Protection Agency, Research Triangle Park, North Carolina.
1988.
2. Development of the 1985 NAPAP Emissions Inventory. Prepared by Alliance
Technologies Corporation for the U.S. Environmental Protection Agency,
Research Triangle Park, North Carolina. 1989.
3. Modica, L., D. Dulleba, R. Walters, and J. Langstaff. Flexible Regional
Emissions Data System (FREDS) Documentation for the 1985 NAPAP Emissions
Inventory. Prepared by Alliance Technologies Corporation for the U.S.
Environmental Protection Agency, Research Triangle Park, North Carolina.
. A87-342. January 1988.
4. Walters, R. L. Modica, and D. Fratt. 1985 NAPAP Emissions Inventory
Allocation Factors. Prepared by Alliance Technologies Corporation for
the U.S. Environmental Protection Agency, Research Triangle Park, North
Carolina. A88-471. November 1988.
5. Memorandum from Phil Lorang, Chief, Technical Support Staff, U.S.
Environmental Protection Agency, Ann Arbor, Michigan, to Gene Durman,
U.S. EPA Office of Policy Analysis. Possible Running Loss and Excess
Evaporative Emission Estimates for the SAI Work. August 31, 1988.
6. Wagner, J., R. Walters, L. Maiocco, and D. Neal. Development of the 1980
NAPAP Emissions Inventory. EPA-600/7-86-057a, U.S. Environmental
Protection Agency, Research Triangle Park, North Carolina.
December 1986. page C-16.
7. Chun, K.C. Uncertainty Data Base for Emissions Estimation Parameters:
Area Source Supplement to Interim Report. ANL/EES-TM-353, Argonne
National Laboratory, Argonne, Illinois. April 1988.
8. Highway Statistics. Federal Highway Administration.
9. Passenger Car Fuel Economy: EPA and Road. EPA-460/3-80-010, U.S.
Environmental Protection Agency, Ann Arbor, Michigan. April 1980.
10. Compilation of Air Pollutant Emission Factors, Fourth Edition and
Supplements. AP-42, U.S. Environmental Protection Agency, Research
Triangle Park, North Carolina. September 1985.
11. Procedures for the Preparation of Emission Inventories for Precursors of
Ozone - Volume I, Third Edition. EPA-450/4-88-021, U.S. Environmental
Protection Agency, Research Triangle Park, North Carolina.
December 1988.
43
-------
APPENDIX A
STATE AND PROVINCE EMISSIONS FOR A TYPICAL SUMMER WEEKDAY
-------
ABBREVIATIONS USED IN APPENDIX A
Anth. = Anthracite
Bit. = Bituminous
Comb. = Combustion
Comm/Inst. = Commercial/Institutional
Dist. = Distillate
Distil. = Distillation
EFR = External Floating Roof
Ems. = Emissions
Ext. = External
Furn. = Furnaces
Ind. = Industrial
Int. = Internal
Mfg. = Manufacturing
Nat. = Natural
Oper. = Operations
Petr. = Petroleum
Pharm. = Pharmaceuticals
POTWs = Publicly-Owned Wastewater Treatment Works
Proc. = Processing
Prod. = Production
Recip. = Reciprocating Engines
Res. = Residential
Sinter. = Sintering
Subm. = Submerged
Term. = Terminals
TSDFs = Treatment, Storage, and.Disposal Facilities
Turb. = Turbines
Util. = Electric Utility
WW = Wastewater
NOTE:
Emissions estimates in the following tables are given to three decimal
places in order to cover small emission categories. As a result,
emissions for some of the larger categories are expressed in up to seven
significant digits. These estimates are not accurate to seven digits,
but only to two or three digits.
-------
;.MI33iCNS i TONS/DAY)
10:36 MONDAY, MAY
DESCRIPTION
Solvent Metal Cleaning
Printing and Publishing
EFR Tanks - Gasoline
Bulk Gas Term.- Not Balanced
Styrene-Butadiene Rubber Mfs.
Polyethylene Mfg.
Rubber Tire Mfg.
Automobile Surface Coating
Beverage Can Surface Coating
Misc. Surface Coating
Util. Ext. Comb. - Coal
Util. Ext. Comb. - Oil
Util. Ext. Comb. - Natural Gas
Ind. Ext. Comb. - Other
Comm./lnst. Comb. - Oil
Comm./Inst. Comb. - Gas
Internal Comb. • Aircraft
Waste Disposal
Ind. Int. Comb. - Gas Turb.
Ind. Int. Comb. - Gas Recip.
Util. Int. Comb. - Oil Turb.
Util. Int. Comb. - Oil Recip.
Ind. Ext. Comb.- Oi 1 ,>100MMBtu/h
Ind. Ext. Comb.- Gas,>100MM8tu/h
Ind. Ext. Comb.- Gas,<100MMBtu
i i A . c _U
POO
1
2
7
10
J2
24
30
53
34
37
50
51
52
57
59
60
2_;
64
72
73
74
75
87
88
90
;t~'.jr.r.ec:-. •
1985
UNAOJ.
CO
2.829
0.000
0.000
0.000
O.OCO
O.COO
0.000
0.000
0.000
0.000
o.ooc
0.241
5.120
0.089
0.000
0.163
0.100
: . .633
9.510
0.001
0.000
0.001
0.008
0.578
0.072
0.016
1985
•JflACu.
NQX
0.449
0.000
0.002
0.000
0.000
O.'JOO
0.000
~i . OCO
J.OOO
0.000
••j.ooo
7.251
46.617
0.619
0.122
1.753
0.442
3.7=3
0.990
\ 0.002
0.000
0.017
0.032
6.179
0.490
0.060
1985
•JNACJ.
VOC
4.740
0.396
0.079
1 .140
0.442
0.123
0.395
0.7^2
0.963
1.149
1.587
0.028
1.192
0.001
0.000
O.C36
0.002
~ . 369
0.081
0.000
O.OCO
0.000
0.000
0.038
0.001
0.000
1985 FULLY
AC „' LISTED
CO
2.829
0.000
0.000
0.000
n.ooo
0.000
0.000
0. -32
O.OCO
0 . 000
c.ooo
0.241
5.120
0.089
0.000
0.153
0.100
).i33
9.510
0.001
0.000
0.001
0.008
0.578
0.072
0.016
1935 FULLY
AS-L'jTEj
NOX
0.449
0.000
0.002
0.000
0.000
0.000
0.000
:.ooo
0.000
0.000
0 . 000
7.251
46.617
0.619
0.122
1 . "63
0.442
5.TS3
0.990
0.002
O.COO
0.017
0.032
6.179
0.490
0.060
1935 FULL:'
AD J'J3 ic'j
VOC
4.740
0.396
0.079
1.140
0.442
0.123
0.395
~. . "-i
0.963
i. iu9
:.:S7
0.023
1.192
0.001
0.000
O.C36
O.OC2
0.369-
0.081
0.000
0.000
0.000
0.000
0.038
0.001
0.000
19.364
68.796
13.517
19.364
68.796
13.517
-------
- Nt'Ji ^:A
DESCRIPTION
VIC^C CT A "*
.__. .-_.,,.,-,,.-... -. . NEDS STAi
DESCRIPTION
Res. ruel - Ancn. Coal
Res. Fuel - Disc. Gil
Res. Fuel - Natural Gas
Res. Fuel - Wood
Comm/Inst. Fuel - Anth. Coal
Comm/Inst. Fuel - Dist. Oil
Comm/Inst. Fuel • Res;d. Oil
Comm/Inst. Fuel - Natural Gas
,-nr
0.000
0.000
0.000
o.:oo
0.000
0.000
0.000
0.000
1985 FULLY
ADJUSTED
NOX
199.203
1985 FULLY
ADJUSTED
MCX
0.001
0.413
0.197
0.133
0.269
2.584
0.915
1.957
0.313
2.073
4.826
0.118
0.009
1.188
5.193
3.395
1.018
0.112
0.236
2.451
0.268
0.276
0.000
0.247
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000 .
0.000
0.000
• "30
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0 . 000
1935 FULLY
AC JUSTED
VOC
361.344
1565 FULL:"
ADJUSTED
vcc
0.003
0.032
0.000
2.405
0.002
0.076
0.023
0.050
0.001
0.137
0.048
2.086
0.002
6.262
16.923
0.552
0.247
0.280
0.332
1.898
0.067
6.058
53.399
1.958
37.948
14.229
11.538
25.083
43.756
7.490
1.007
14.885
3.016
3.426
- ;_-_;
0.495
0.894
1.023
' .733
49.069
97.518
0.406
5.413
-------
EMISSIONS (TONS/DAr) 10.36 MONDAY, MAY
DESCRIPTION
Fugitives from SOCM1
Bulk Terminals and Bulk Plants
Process Ems. - Bakeries
Process Ems. - Pharm. Mfg.
Proc. Ems.- Synth. Fibers Mfg.
Crude Oil/Nat.Gas Prod. Fields
Hazardous Waste TSOFs
sec
102
103
105
106
107
108
109
1985
UNADJ.
CO
0.000
0.000
0.000
0.000
0.000
0.000
0.000
1935
UNADJ.
NOX
0.000
0.000
0.000
0.000
0.000
0.000
0.000
1985
UNAOJ.
voc
7.311
9.526
1.327
1.082
0.255
2.692
14.224
1985 FULLY
ADJUSTED
CO
0.000
0.000
0.000
0.000
0.000
0.000
0.000
1985 FULLY
ADJUSTED
NOX
0.000
0.000
0.000
0.000
0.000
0.000
0.000
1985 FULLY
ADJUSTED
VCC
7.311
15.165
1.327
1.082
0.255
2.692
17.C69
261.257 23.133 *13.169 :7Q.i43 23.251
-------
TONS/DAY)
10.56 MONDAY, MAY 2, ;9£9
NEDS ST
DESCRIPTION
Petroleum Refinery Fugitives
Styrene-Butadiene Rubber Mfg.
Ptr. Refinery Vacuum Distil.
Automobile Surface Coatinc
Util. Ext. Comb. - Coal
Util. Ext. Comb. - Oil
Util. Ext. Comb. - Natural Gas
Comm./Inst. Comb. - Oil
Comm./Inst. Comb. - Gas
Cogeneration - Otrier
Ind.Ext.Comb.- Oil,<100MM8tu/h
Ind.Ext.Comb.- OiI,>100MM8tu/h
Ind.Ext.Comb.- Gas,>100MMBtu/h
Ind.Ext.Comb.-Cogeneration
Ind.Ext.Comb.- Gas,<100MMBtu/h
, A 1 C I
POO
20
22
27
33
50
51
52
59
60
84
85
87
88
89
90
.wUC-'je'.aUc
1985
UNADJ.
CO
31.704
0.000
0.000
7.009
0.000
2.444
0.911
0.111
0.033
0.014
0.232
0.070
0.253
0.041
0.494
0.362
ITi L/iiCLil.
1985
UNADJ.
NOX
5.002
0.000
0.000
2.751
0.000
85.527
11.838
1.523
0.585
0.095
7.485
1.068
2.896
0.281
13.611
1.650
JK 7 -SU i N 1
1985
UNADJ .
VOC
2.266
3.071
0.684
0.192
14.763
0.285
0.207
O.OC2
0.037
0.000
0.025
0.081
0.041
0.000
0.009
0.023
1935 FULLY
ADJUSTED
CO
31.704
0.000
0.000
7.009
0.000
2.444
0.911
0.111
0.033
0.014
0.282
0.070
0.253
0.041
0.494
0.362
1985 FULLY
ADJUSTED
NOX
5.002
0.000
0.000
2.751
0.000
85.527
11.838
1.5Z3
0.585
0.095
7.435
1.068
2.896
0.281
13.611
1.650
1985 FULLY
ADJUSTED
VOC
2.266
3.071
0.684
0.192
14.763
0.285
0.207
O.OC2
0.037
0.000
O.C25
0.081
0.041
0.000
0.009
0.023
43.727
134.312
21.694
43.727
21.694
-------
iHl S3 IONS (TCNS/DA'f )
10,36 MGHDAY, MAY 2, '.
1985
JNAOJ.
DESCRIPTION SCC CO
ALL 345.570
1985
DESCRIPTION
Res. Fuel - Anth. Coai
Res. Fuel - Oist. Oi I
Res. Fuel - Natural Gas
Res. Fuel • Wood
Comm/Inst. Fuel - Anth. Coal
Comm/Inst. Fuel - Bit. Coal
Comm/!nst. Fuel - Ois:. Oil
Comm/Inst. Fuel - Natural Gas
Ind. Fuel - Bit. Coal
Ind. Fuel - Dist. Oil
Ind. Fuel - Natural Gas
Incineration - Residential
Incineration - Industrial
Incineration - Comm/Inst.
Open Burning - Residential
Off-Highway Gas Vehicles
Off-Highway Diesel Vehicles
Railroad Locomotives
Aircraft - Military
Aircraft - Civil
Aircraft - Commercial
Vessels - Diesel
Vessels - Residual Oil
Vessels - Gasoline
Gasoline Marketed
Managed Burning - Prescribed
Agricultural Field Burning
Structural Fires
Degreasing
D rye lean ing
Graphic Arts/Printing
Rubber and Plastic Mfg.
Architectural Coating
Auto Body Repair
Paper :.3-iry;
Fabricated Metals
Machinery Mfg.
Furniture Mfg.
"1st '-'cod '--^ducts
Electrcal Equip. Mfg.
Ship Building and Repair
Misc. Ind. Mfg.
Misc. Ind. Solvent Use
SCC
1
3
5
6
7
8
9
11
14
16
18
21
22
23
24
39
44
45
46
47
48
50
51
52
54
61
62
64
78
79
80
81
82
83
1C
86
87
88
*9
91
92
93
95
UNADJ.
:o
0.003
0.019
0.010
2.429
0.001
0.018
0.060
0.054
Z . 053
0.040
0.805
0.774
0.053
0.196
7.620
44.553
1.678
0.067
2.310
3.859
0.195
0.037
0.003
9.484
0.000
0.000
0.000
1.833
0.000
0.000
0.000
0.000
0.000
0.000
:.3oc
0.000
0.000
0.000
l.COQ
0.000
0.000
0.000
0.000
1985
UN ADJ.
NOX
C7=mjbiL:
1985
JNAOJ.
VOC
63.880 63.580
1985 ;?65
UNAD.I. UNAOJ.
XCX
0.000
0.067
0.049
0.029
0.011
0.031
0.238
0.267
C.iSI
0.163
3.225
0.002
0.007
0.067
0.455
1.558
5.512
0.191
0.490
0.074
0.071
0.104
0.101
0.121
0.000
0.000
0.000
0.042
0.000
O.COO
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
VOC
.0.000
0.005
0.000
0.528
0.000
0.001
O.C07
0.006
0.001
0.311
0.030
0.050
0.007
0.016
2.402
5.078
0.896
0.046
1.226
0.215
0.055
0.026
0.009
2.660
8.458
0.000
0.000
0.337
1.692
2.032
1.532
5.231
4.238
2.389
0.249
0.067
0.379
0.003
0.010
7.078
17.115
19S5 FULLY
ADJUSTED
CO
435.648
1965 FULLY
ADJUSTED
CO
0.003
0.019
0.010
2.429
0.001
0.018
C.?60
0.054
o.csa
0.040
0.805
0.774
0.053
0.196
7.620
44.553
1.678
0.067
2.310
3.359
0.195
0.037
0.003
16.122
0.000
0.000
0.000
1.838
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
o.coc
0.000
0.000
0.000
o.oco
1935 FULLY
ACJU^TEO
NCX
52.926
•C85 FULLY
ADJUSTED
10X
0.000
0.067
0.049
0.029
0.011
0.031
C.233
0.267
C.451
0.168
3.225
0.002
0.007
0.067
0.455
1.558
5.512
0.191
0.490
0.074
0.071
0.104
0.101
0.205
0.000
0.000
0.000
0.042
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
1 985 FULLY
AD-USTEC
VOC
37.586
1985 FUL.f
ADJUSTED
vcc
0.000
O.OC5
0.000
0.523
0.000
0.001
0.007
O.G06
" .-01
0.011
0.030
0.050
0.007
0.016
2.402
5.073
0.396
0.046
1.226
0.215
O.C55
0.026
0.009
4.523
12.451
0.000
0.000
0.337
1.592
2.032
1.532
5.231
7.2S9
2.389
0.249
0.067
0.379
0.003
0.010
7.078
17.270
-------
EMISSIONS (TONS/DAY) 10.36 MONDAY, :-iAY 5,
fiEDS STATE
DESCRIPTION
POTWS
Cutback Asphalt Paving Oper.
Fugitives from SOCMI
Sulk Terminals and Sulk Plants
Petroleum Refinery Fugitives
Process Ems. - Bakeries
Process Ems. - Pharm. Mfg.
Proc. Ems.- Synth, riberj ,'i*c.
Crude Oil/Nat.Gas Prod. Fie'.ds
Hazardous Waste TSDFs
1 c LUl
sec
100
101
102
103
104
105
106
107
108
109
;t=ue'.aware
1935
UK AD J .
CO
0.000
0.000
0.000
0.000
0.000
0.000
0.000
o.oco
0.000
0.000
CM I C'jtJKT—1
1985
UNADJ .
NOX
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
. 0.000
fUNf1'j3iL± • - •
1985
UNADJ .
VOC
0.241
2.764
6.402
2.982
20.385
•J.346
0.709
25.946
0.140
0.201
1935 FULLY
AC J'JSTEO
CO
0.000
0.000
0.000
0.000
0.000
0.000
o.oco
o.:oo
0.000
0.000
1985 FULLY
\Q J':"T"D
NOX
0.000
0.000
o.occ
0.000
o.coo
O.w'OO
0.000
0 . 000
0.000
o.oco
:9S5 FULLY
ADJUSTED
VOC
0,241
2.764
6.402''
4.533
20.385
0.346'
0.709
25.946
0.140
0.241
76.164 13.344 128.873 32.803 13.423 139.474
-------
EMISSIONS (TONS/DAY) 10.36 MONDAY, MAY 8,
-- Nfe'JS -51 AlC
ujuc-ji
S LI 1
1
ct or cc
985
UNADJ.
DESCRIPTION
Printing and Publishing
Util. Ext. Comb. -
Comm./Inst. Comb.
Comm./Inst. Comb.
Conm./lnst. Comb.
Waste Disposal
Ind. Ext. Comb. - Oil
Oil
- Coal
- Oil
- Gas
,>100MMBtu/h
POD
.
2
51
58
59
60
64
37
0
0
0
0
0
0
5
0
CO
.000
.000
.050
.078
.148
.032
.633
.000
j i uffio ; a
1985
UNADJ.
NOX
0.000
0.009
0.573
1.173
1.271
0.143
0.482
0.000
LA; c'jUKT -i-0!Nl
1985
UNADJ.
VOC
0.027
1.733
0.014
0.005
0.041
0.001
0.047
0.000
1985
rULLY
ADJUSTED
0
0
0
0
0
0
5
0
CO
.000
.000
.050
.078
.148
.032
.633
.000
1985
FULLY
ADJUSTED
NOX
0
0
0
1
1
0
0
c
.000
.009
.573
.173
.271
.143
.482
.000
1935 r'ULLY
ADJUSTED
VOC
0.027
1.733
0.014
0.005
0.041
0.001
0.047
0.000
5.942 3.654 1.871 5.942 3.654 1.371
-------
EMISSIONS vTCNS
10.36 MONDAY, MAY 3, i"S9
NtUS SlAi
DESCRIPTION
._--.._....... klCPlCCTATC
.. ....--..-...... .___ NcDS STATE
DESCRIPTION
Res. Fuel - Bit. Coal
Res. Fuel - Dist. Oil
Res. Fuel - Natural Gas
Res. Fuel - Wood
Comm/Inst. Fuel - Bit. Coal
Comm/Inst. Fuel - Dist. Oil
Comm/Inst. Fuel • Resid. Oil
Comm/Inst. Fuel - Natural Gas
Ind. Fuel • Residual Oil
Ind. Fuel - Natural Gas
Incineration - Residential
Incineration - Comm/Inst.
Off-Highway Gas Vehicles
Off-Highway Diesel Vehicles
Railroad Locomotives
Aircraft - Military
Aircraft - Civil
Aircraft - Commercial
Vessels - Gasoline
Gasoline Marketed
Structural Fires
Degreasing
D rye lean ing
Graphic Arts/Printing
Rubber and Plastic Mfg.
Architectural Coating
Fabricated Metals
Machinery Mfg.
Furniture Mfg.
Flat Wood Products
Electrcal Equip. Mfg.
Misc. Ind. Mfg.
Misc. Ind. Solvent Use
Fugitives from SOCMI
c CCUt=UI
sec
istnc: or
1985
UNADJ.
CO
tciumm 3
1985
UNAOJ.
NOX
LAI cljUKI=rUB ILZ
1985
UNADJ.
VOC
ALL 156.210 32.330 35.000
pnnc — n io^r-i/-* s*£ ?* s^l t imK ia PftTCPHDV — kJOUMnHTI P
LUUt— U IStriC" OT uOt UfTiD 1 a LM t CuUK I -NUNPIUO I LC
1985 1985 1985
UNADJ. UNADJ. UNAOJ.
sec
2
3
5
6
8
9
10
11
17
18
21
23
39
44
45
46
47
48
52
54
64
78
79
80
82
85
86
87
88
89
91
93
95
102
CO
0.138
0.006
0.019
0.215
0.116
0.099
0.027
0.184
l.OCO
0.231
1.071
1.889
109.181
1.918
1.426
0.092
1.278
8.916
0.866
0.000
2.540
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
NOX
0.004
0.020
0.094
0.002
0.195
0.394
0.296
0.920
0.003
1.700
v 0.004
0.653
3.818
6.302
4.059
0.019
0.024
3.265
0.011
0.000
0.058
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
O.QOO
0.000
VOC
0.015
0.001
0.000
0.046
0.008
0.011
0.009
0.023
c.coo
0.020
0.070
0.156
12.444
1.024
0.985
0.048
0.071
2.528
0.243
6.892
0.466
0.166
4.866
5.761
4.316
0.583
0.097
0.010
0.108
0.014
0.003
2.305
13.753
0.013
1985 FULLY
ADJUSTED
CO
20.767
1985 FULLY
ADJUSTED
CO
0.133
0.006
0.019
0.215
0.116
0.099
0.027
0.184
0.000
0.231
1.071
1.889
109.181
1.918
1.426
0.092
1.278
8.916
1.300
0.000
2.540
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
Z\-['< Terminalj i-.d Z-ji.^ .-'.anrs 'C3 C.CCC ^.CCO I.-^j O.OGC
Process Ems. - Bakeries
105
0.000
130.214
0.000
21.851
0.563
58.677
0.000
130.647
1985 FULLY
ADJUSTED
NCX
26.495
1985 FULLY
ADJUSTED
rtCX
0.004
0.020
0.094
0.002
0.195
0.394
0.296
0.920
0.003
1.700
0.004
0.653
3.818
6.302
4.059
0.019
0.024
3.265
0.016
0.000
0.058
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
o.ooc
0.000
•: . JUG
0.000
21.856
1985 FULLY
ADJUSTED
VOC
50.908
1985 FULLY
ADJUSTED
VOC
0.015
0.002
0.000
0.047
0.009
0.012
0.009
0.023
O.CCO
0.020
0.070
0.157
12.444
1.025
0.986
0.049
0.071
2.528
0.365
10.008
0.467
0.166
4.867
5.762
7.339
0.583
0.098
0.011
0.108
0.015
0.004
2.305
13.377
0.013
1 . j36
0.563
65.603
-------
HHiS3;ONS (TONS/DAY;
10.36 MONDAY, MAY 2., \rc,9
DESCRIPTION
Solvent Metal Cleaning
Printing and Publishing
Fixed Roof Tanks - Crude Oil
EFR Tanks - Crude OiI
EFR Tanks - Gasoline
Bulk Gas Term.- Not Balanced
Petroleum Refinery Fugitives
Polyethylene Mfg.
Petr. Refinery WW Treatment
Ptr. Refinery Vacuum Distil.
Automobile Surface Coating
Beverage Can Surface Coating
Misc. Surface Coating
Coke Oven Byproduct Plants
Iron/Steel Blast Furn..Sinter.
Marine Vessel Loading
Util. Ext. Comb. - Coal
Comm./Inst. Comb. - Coal
Cogeneration - Other
Ind.Ext.Comb.- Oil,>10CMMBtu/h
Ind.Ext.Comb.- Gas,>100MMBtu/h
Ind.Ext.Comb.- Gas,<100MMBtu/h
: l A 1 c 1
POO
1
2
4
6
7
10
20
24
26
27
. 33
34
37
39
41
43
50
58
84
87
88
90
,uut=\2ncucxy
1985
UNAOJ.
CO
12.365
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
20.751
0.000
0.000
0.000
0.047
0.000
0.000
6.320
0.335
0.150
0.053
0.036
1.238
1985
UNAOJ.
NOX
21.839
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
3.592
0.000
0.000
0.000
0.000
0.000
0.000
199.838
0.685
»* 0.200
0.557
0.565
3.134
17=-'Ut« I
1985
UN ADJ.
VOC
26.500
0.079
0.384
0.199
0.628
0.467
2.298
1.224
1.745
0.587
1.133
6.698
0.165
3.541
0.054
0.000
6.189
0.775
0.052
0.005
0.001
0.000
0.005
1985 FULLY
ADJUSTED
CO
12.365
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
20.751
0.000
0.000
0.000
0.047
0.000
0.000
6.320
0.335
0.150
0.053
0.036
1.238
1985 FULLY
ADJUSTED
NOX
21.839
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
3.592
0.000
0.000
0.000
0.000
0.000
0.000
199.838
0.685
0.200
0.557
0.565
3.134
1985 FULLY
ADJUSTED
VOC
26.500
0.079
0.384
0.199
0.628
0.467
2.298
1.224
1.745
0.537
1.133
6.698
0.165
3.541
0.054
O.OCO
6.189
0.775
0.052
0.005
0.001
0.000
0.005
41.795
230.410
52.736
41.795
230.410
52.736
-------
cMISSiCNS (TOUS/DAY)
10.56 MONDAY, HAY 3, i985
DESCRIPTION
DESCRIPTION
Res. Fuel - Anth. Coal
Res. Fuel - Sit. Coal
Res. Fuel - Dist. Oil
Res. Fuel • Natural Gas
Res. Fuel - Wood
Comm/Inst. Fuel - Anth. Coal
Comm/Inst. Fuel - Sit. Coal
Comm/Inst. Fuel - Dist. Oil
Comm/Inst. Fuel - Natural Gas
Ind. Fuel - Bit. Coal
Ind. Fuel - Dist. Oil
Ind. Fuel • Natural Gas
Incineration - Residential
Incineration - Industrial
Incineration - Comm/Inst.
Open Burning - Residential
Open Burning - Industrial
Open Burning - Comm/Inst.
Off-Highway Gas Vehicles
Off-Highway Diesel Vehicles
Railroad Locomotives
Aircraft - Military
Aircraft - Civil
Aircraft - Commercial
Vessels - Diesel
Vessels - Gasoline
Gasoline Marketed
Forest Wildfires
Structural Fires
Degreasing
D rye lean ing
Graphic Arts/Printing
Rubber and Plastic Mfg.
Architectural Coating
ALICO 3oay ".epair
Moto Vehicle Mfg.
Paper Coating
Fabricated Metals
''schinery Mfg.
Furniture Mfg.
Flat Wood Products
Other Trans. Equip. Mfg.
Electrcal Equip. Mfg.
1985
UN ADJ.
SCC CO
ALL 823.740
TATE CODE=
-------
EMISSIONS (TONS/DAY)
!6 MONDAY, MAY 3, 1989
DESCRIPTION
Ship Building and Repair
Misc. Ind. Mfg.
Misc. Ind. Solvent Use
POTUs
Cutback Asphalt Paving Oper.
Fugitives from SOCHI
Sulk Terminals and Bulk Plants
Petroleum Refinery Fugitives
Process E.iis. - Bakeries
Crude Oil/Nat.Gas Prod. Fields
Hazardous Waste TSDFs
lit LU
sec
92
93
95
100
101
102
103
104
105
108
109
uc=s.enti:cKy
1985
UNADJ.
CO
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
LAI EUUK7=NU
1985
UNADJ.
NOX
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
NMUblLC •••
1985
UNADJ.
VOC
0.042
8.146
40.429
0.094
4.253
O.C45
8.746
31.871
0.607
5.887
0.124
1985 FULLY
ADJUSTED
CO
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
1985 FULLY
ADJUSTED
NOX
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
1985 FULLY
ADJUSTED
VOC
0.042
3.146
40.793
0.094
4.253
0.045
11.020
31.37:
0.607
5.887
C.I 49
187.215
122.086
200.490
190.297
122.126
217.932
-------
EMISSIONS (TOMS/DAY)
10.36 MONDAY, MAY 3, 1939
DESCRIPTION
Fixed Roof Tanks • Crude Oil
EFR Tanks - Gasoline
Pulp/Paper - Recovery Furnace
Util. Ext. Comb. - Oil
Cemm./Inst. Comb. - Oil
Comm./Inst. Comb. - Gas
Waste Disposal
Cogeneration - Other
Ind.Ext.Comb.- OiI,>100MMBtu/h
Ind.Ext.Comb.- Gas,<10CMMBtu/h
. SFAlt
POO
4
7
42
51
59
60
64
84
87
90
: uuut=Maine
1985
UNADJ.
CO
0.000
0.000
0.000
10.343
0.496
0.014
0.009
0.000
0.070
5.577
8.414
LAI tliUKI=>^
1985
UNADJ.
NOX
0.000
0.000
0.000
0.669
6.653
0.167
0.001
0.000
2.446
8.407
5.976
JIN I
1985
UNADJ.
VOC
0.002
0.008
0.876
1.024
0.116
0.000
0.001
0.000
0.008
1.524
1.812
1985 FULLY
ADJUSTED
CO
0.000
0.000
0.000
10.343
0.496
0.014
0.009
0.000
0.070
5.577
8.414
1985 FULLY
ADJUSTED
NOX
0.000
0.000
0.000
0.669
6.653
0.167
0.001
0.000
2.446
8.407
5.976
19o5 FULLY
ADJUSTED
VOC
0.002
0.008
0.376
1.024
0.116
o.ooo'
0.001
0.000
0.008
1.524
1.812
24.923
24.321
5.375
24.923
24.321
5.375
-------
EMISSIONS
DESCRIPTION
Res. Fuel
Res. Fuel
Res. Fuel
Res. Fuel
Res. Fuel
Comm/Inst
Comm/Inst
Comm/Inst
Comm/Inst
Ind. Fuel
Ind. Fuel
Ind. Fuel
Ind. Fuel
Incineration
Incineration
Incineration
Open Burning
Open Burning
Open Burning
Anth. Coal
Bit. Coal
Dist. Oil
Natural Gas
Wood
Bit. Coal
Disc. Oil
Resid. Oil
Narjral 3as
Coal
Fuel
Fuel
Fuel
Fuel
- Anth
• Coke
• Dist. Oil
• Natural Gas
Residential
Industrial
Comm/Inst.
Residential
Industrial
Comm/Inst.
Off-Highway Gas Vehicles
Off-Highway Diesel Vehicles
Railroad Locomotives
Aircraft - Military
Aircraft - Civil
Aircraft - Commercial
Vessels - Diesel
Vessels • Residual Oil
Vessels - Gasoline
Gasoline Marketed
Agricultural Field Burning
Structural Fires
Degreasing
0rye lean ing
Graphic Arts/Printing
Architectural Coating
Auto Body Repair
Moto Vehicle Mfg.
';c2r :^3t:'r.-;
Fabricated Metals
Machinery Mfg.
Furni ture Mfg.
Flat Wood Products
sec
ALL
STATE
sec
1
2
3
5
6
8
9
10
11
13
15
16
18
21
22
23
24
25
26
39
44
45
46
47
48
50
51
52
54
62
64
78
79
80
82
83
34
1C
86
87
38
89
1985
UNAOJ.
CQ
321.520
CODE=Maine
1985
UNADJ.
CO
0.'.29
0.022
0.170
0.007
28.423
0.005
0.141
0.084
O.Oli
0.001
0.005
0.070
0.051
12.775
0.028
0.374
17.272
0.254
0.025
93.713
1.323
1.097
1.247
6.707
1.461
0.187
0.000
6.240
0.000
0.000
2.306
0.000
O.GOO
0.000
0.000
0.000
0.000
- '-«
0.000
o.coo
o.coo
o.oou
1935
uNAt/J .
;icx
;•;«=
•JNAOJ .
VCC
71.280 68.790
CATEGOKY=rtONMOB I LE — •
1985 1 935
•JNAOJ. UNADJ.
NCX
0.004
C.OQO
0.611
0.033
0.341
0.008
3.563
0.921
0.0 77
0.024
0.010
0.294
0.233
0.047
0.004
0.129
1.032
0.014
0.001
3.277
4.345
3.123
0.264
0.128
0.534
0.533
0.009
0.079
0.000
0.000
0.053
0.000
0 . 000
0.000
.,.-00
0.000
0.000
0 . 000
0.000
o.coo
0.000
0.000
VCC
0.014
0.002
0.046
0.000
6.186
0.000
0.016
0.023
O.GQ2
0.000
0.000
0.019
0.002
0.834
0.003
0.031
5.444
0.072
n.ooa
10.681
0.706
0.758
0.662
0.374
0.414
0.133
0.000
1.750
10.066
0.000
0.423
3.547
2.476
2.572
:'. -J3
5.781
3.015
0.04?
0.459
0.328
0.693
0.200
•76: /UL1Y
ADJUSTED
CO
338.520
1985 FULLY
ADJUSTED
CO
0.129
0.022
0.170
0.007
28.423
0.005
0.141
0.084
0.016
0.001
0.005
0.070
0.051
12.775
0.028
0.374
17.272
0.254
0.025
93.713
1.323
1.097
1.247
6.707
1.461
0.187
0.000
12.481
0.000
0.000
2.306
0.000
O.COO
0.000
j. ^JG
0.000
0.000
0 . 000
O.DOO
0.000
0.000
0 . jOO
;•-.* -;••
«Dn JS7ED
•JOX
58.039
!?35 ?:JLLY
ADJUSTED
:JOX
0.004
0.000
0.611
0.033
0.341
0.008
0.363
0.921
C.077
0.024
0.010
0.294
0.233
0.047
0.004
0.129
1.032
0.014
O.OC1
3.277
4.345
3.123
0 . 2i4
0.128
0.334
0.533
0.009
0.159
0.000
0.000
0.053
0.000
C.CGO
0.000
J...-JJ
0.000
0.000
0.000
0 . 000
0.000
0.000
J . 000
.0?s _..L .,
AC juSTED
voc
89.150
1935 FULLY
ADJUSTED
VOC
0.014
0.002
0.046
0.000
6.186
0.000
0.016
0.028
0.002
0.000
0.000
0.019
0.002
0.834
0.003
0.031
5.444
0.072
0.008
10.681
0.706
0.758
0 . 662
0.374
0.414
0.133
0.000
3.501
16.025
0.000
0.423
3.547
2. -76
3.572
. -- 0
13.375
3.015
°-:::
o.;59
0.32S
0.693
: . ooo
-------
fHlSStONS i.TOMS/DAY 1
DESCRIPTION
Other Trans. Equip. Mfg.
Electrcal Equip. Mfg.
Ship Building and Repair
Misc. Ind. Mfg.
Misc. Ind. Solvent Use
POTWs
Cutback Asphalt Paving Oper.
Bulk Terminals and Bulk Plants
Process Ems. - Bakeries
Hazardous Waste TSDFs
! i ai c ,
sec
90
91
92
93
05
100
101
1J2
105
109
.-Jt-,iair.e
19S5
IMADJ.
CO
0.000
0.000
0.000
0.000
0.000
o.ono
0.000
:.ooo
0.000
0.000
_,•*: c'jUKl ~
-------
EMISSIONS (TONS/DAY)
;0. jo .10,'iOAT , .1AY
1989
- NtLJb
DESCRIPTION
Solvent Metal Cleaning
Printing and Publishing
Fixed Roof Tanks - Gasoline
EFR Tanks - Crude Oil
EFR Tanks - Gasoline
Polyethylene Mfg.
Paint and Varnish Mfg.
Rubber Tire Mfg.
Automobile Surface Coating
Beverage Can Surface Coating
Paper Surface Coating
Misc. Surface Coating
Coke Oven Byproduct Plants
Iron/Steel Blast Furn., Sinter.
Pulp/Paper - Recovery Furnace
Util. Ext. Comb. - Coal
Util. Ext. Comb. - Oil
Util. Ext. Comb. - Natural Gas
Ind. Ext. Comb. - Other
Comm./Inst. Comb. - Coal
Comm./Inst. Comb. - Oil
Comm./Inst. Comb. - Gas
Waste Disposal
Util. Int. Comb. - Oil Turb.
Util. Int. Comb. - Oil Recip.
Util. Int. Comb. - Gas Turb.
Util. Int. Comb. - Gas Recip.
Cogeneration - Other
Ind. Ext. Comb.- Oi l,>100MMBtu/h
Ind. Ext. Comb.- Gas,>100MM8tu/h
Ind. Ext. Comb.- Gas,<100MMBtu/h
SIAIt I
POD
1
2
5
6
7
24
29
30
33
34
36
37
39
41
42
50
51
52
57
58
59
60
64
74
75
76
77
84
87 '
88
90
1985
UNADJ .
CO
33.614
0.000
0.000
0.000
0.000
0.000
0.000
0.000
o.oco
o.cco
o.oco
0.000
0.000
0.379
0.272
10.893
6.727
1.772
0.444
0.000
0.069
0.239
0.004
8.613
0.202
0.253
0.006
0.161
0.292
0.257
0.325
3.017
a LAieuuKi
1935
UNADJ .
NOX
30.198
o.ooc
0.002
0.000
o.ocn
0.000
0.007
O.QCO
n.coo
0.000
0.116
0.000
0.004
1.425
5.091
0.132
202.972
il . .'-<<.
5.213
* 0.004
0.131
2.730
0.027
3.441
0.877
1.031
0.035
1.183
9.888
3.089
5.799
11.226
1985
Lifj AO J
vcc
10.662
0.161
11.753
0.222
0.006
5.946
0.932
2.376
O.CCO
1.080
11.002
0.044
2.107
0.789
0.002
0.002
0.823
0.372
0.000
0.000
0.010
0.039
0.000
0.058
0.000
0.041
0.000
0.007
0.102
0.066
0.020
0.261
1985 FULLY
CO
33.614
0.000
0.000
0.000
o.eoc
0.000
•i . :oo
a. :oo
:.coo
0.000
0.000
0.000
0.000
0.379
0.272
10.393
6.727
0.444
0.000
0.069
0.239
0.004
8.613
0.202
0.253
0.006
0.161
0.292
0.257
0.325
3.017
1935 :>JLLY
NOX
30.198
a. GOO
0.002
0.000
O.jOO
O.uOO
O.C07
2.300
c.;oc
O.JOO
0.-16
0.000
0.004
1.425
5.091
Z.--.Z2
202.972
ii . : -2
5.213
0.004
6.131
2.730
0.027
3.441
0.877
1.031
0.035
1 .183
9.888
3.089
5.799
11.226
1965 FULLY
VOC
10.662
0. 161
11.753
0.222
j.006
5.94;
0.932
2 . 3 ,"c
").;CO
1.080
11.002
0.044
2.107
0.789
0.002
0.002
0.823
0.372
0.000
0.000
O.C10
0.039
0.000
0.058
0.000
0.041
0.000
0.007
0.102
0.066
0.020
0 . 26.1
67.539
305.761
48.944
67.539
305.761
48.944
-------
(TONS/DAY 1
10.J6 MONDAY, MAY 3, 1939
DESCRIPTION
. . _--- ....... ...... ....... NtUo i
DESCRIPTION
Res. Fuel - Anth. Coal
Res. Fuel - Bit. Coal
Res. Fuel - Dist. Oil
Res. Fuel - Residual Oil
Res. Fuel - Natural Gas
Res. Fuel - Wood
Comm/Inst. Fuel - Anth. Coal
Comm/Inst. Fuel - Bit. Coal
Comm/Inst. Fuel • Dist. Oil
Comm/Inst. Fuel - Resid. Oil
Comm/Inst. Fuel - Natural Gas
Ind. Fuel - Anth. Coal
Ind. Fuel - Bit. Coal
Ind. Fuel - Dist. Oil
Ind. Fuel - Residual Oil
Ind. Fuel - Natural Gas
Ind. Fuel - Wood
Incineration - Residential
Incineration - Industrial
Incineration - Comm/Inst.
Open Burning - Residential
Off -Highway Gas Vehicles
Off-Highway Diesel Vehicles
Railroad Locomotives
Aircraft - Military
Aircraft - Civil
Aircraft - Commercial
Vessels - Coal
Vessels - Diesel
Vessels - Residual Oil
Vessels - Gasoline
Gasoline Marketed
Agricultural Field Burning
Structural Fires
Oegreasing
D rye lean ing
Graphic Arts/Printing
Rubber and Plastic Mfg.
Arcnitecrurai Ccatir.g
Auto Body Repair
Moto Vehicle Mfg.
Paper Coating
Fabricated Metals
1985
UNACJ.
SCC CO
ALL 1204.140
TATE COOE=Maryland
SCC
1
2
3
4
5
6
7
3
7
10
11
13
14
16
17
18
19
21
22
23
24
39
44
45
46
47
48
50
51
52
54
60
62
64
i"3
79
30
21
_£.
83
34
85
36
1985
UN ADJ.
CO
1.921
1.195
0.597
0.008
0.338
9.514
O.COO
0.087
3.570
0.136
0.286
0.000
0.040
1.454
0.179
2.515
0.293
0.680
3.912
2.744
2.313
357.657
37.269
4.565
10.387
19.892
7.717
0.303
0.143
25.603
0.000
77.831
0.000
13.161
0. uOO
0.000
0.000
O.OCO
;.JOQ
0.000
0.000
O.COO
0.000
(.Al tlivJi
1985
UNADJ.
NOX
1985
urJAOj.
voc
362.650 367.660
f™ A TCf*f>D V — UnUMHQ I 1 C
CATcGQR T -NUNMUol Lt
1985 1535
UNAOJ. 'JNAOu.
NOX
0.064
0.040
2.150
0.028
1.690
0.114
0.000
0.146
2.281
1.501
1.430
0.000
0.314
6.136
1.973
13.627
0.176
0.002
0.582
0.950
0.138
12.509
122.437
12.993
2.207
0.382
2.826
0.865
4.280
0.327
0.000
2.224
0.000
0.305
O.uUO
0.000
0.000
0.000
0.000
0.000
0.000
o.coc
0.000
VCC
0.213
0.133
0.163
0.002
0.000
2.071
0.000
0.007
0.06-"
0.046
0.036
0.000
0.001
0.405
0.016
0.148
0.063
0.044
0.516
0.227
0.729
40.764
19.906
3.156
5.515
1.111
2.188
0.216
0.393
7.183
57.963
10.674
0.000
7.i30
i H . /"65
17.700
11.136
17.230
30.226
13.094
0.211
13.323
2.050
1°85 FULLY
AOuUSrED
CO
2002.090
1985 FULLY
ADJUSTED
CO
1.921
1.-.95
0.597
0.008
0.338
9.514
O.COO
0.087
;.j~o
0.136
0.286
0.000
0.040
1.454
0.179
2.515
0.293
0.680
3.912
2.744
2.313
357.657
37.269
4.565
10.387
19.892
7.717
0.303
0.143
43.525
0.000
77.831
0.000
12.161
•j . 000
0.000
0.000
J.OOO
•-JGO
0.000
0.000
0.000
u.ooo
'985 FULLY
ADJUSTED
NOX
303.210
1985 FULLY
50JUS7SD
UGX
0.064
O.C40
2.150
0.023
1.690
0.114
o.ooc
0.146
2.23:
1.501
1.430
O.OCO
0.314
6.136
1.973
13.627
0.176
0.002
0.5S2
0.950
0.138
12.509
122.437
12.993
2.207
0.382
2.826
0.865
4.230
0.556
0.000
2.224
0.000
0.305
0.000
O.OCO
0.000
o.oec
- — •
0.000
O.OCO
O.OCO
O.OCO
1985 FULLY
ADjUS'cu
VCC
498.662
1985 FU'-L;
ADJUSTS-:
VCC
0.213
0.133
0.163
0.002
0.000
2.071
O.OCO
0.007
0 . Oc7
0.046
0.036
0.000
0.001
0.405
0.016
0.148
0.063
0.044 .
0.51*
0.227
0.729
40.764
19.906
3.156
5.513
1.111
2.188
0.216
0.393
12.211
84.626
10.674
0.000
2.429
i 4 . Tc j
17.700
11.136
17.230
r ;
18.094
0.21;
13.323
2.050
-------
EMISSIONS (TONS/DAY)
iO.56 MONDAY, MAY d, 1939
DESCRIPTION
Machinery Mfg.
Furniture Mfg.
Flat Wood Products
Other Trans. Equip. Mfg.
Electrcal Equip. Mfg.
Ship Building and Repair
Misc. Ind. Mfg.
Misc. Ind. Solvent Use
POTUs
Cutback Asphalt Paving Oper.
Fugitives from 50CMI
Bulk Terminals and Sulk Plants
Process Ems. - Bakeries
Process Ems. - Pharm. Mfg.
Proc. Ems.- Synth. Fibers Mfg.
Crude Oil/Nat.Gas Prod. Fields
Hazardous Waste TSOFs
ilt LUI
sec
87
83
89
90
91
92
93
55
100
101
102
103
105
106
107
103
109
ut=Maryiana
1985
UNADJ.
CO
0.000
0.000
0.000
0.000
0.000
o.oco
0.000
0.000
0.000
0.000
0.000
o.oco
0.000
0.000
0.000
0.000
0.000
LAI tljUK7=Nt
1935
UNADJ.
NOX
0.000
0.000
0.000
0.000
o.ooc
0.000
0.000
0.000
a. ooo
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
jNnubiL: —
1985
UNADJ.
voc
2.300
3.942
0.507
0.082
0.948
0.152
26.730
104.106
0.366
15.445
2.217
11.254
2.135
0.398
0.255
0.541
1.316
1935 FULLY
ADJUSTED
CO
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
1935 FULLY
ADJUSTED
NOX
0.000
o.coo
0.000
0.000
0.000
0.000
0.000
o.oco
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
1935 FULLY
ADJUSTED
voc
2.300
3.940
0.510
0.080
0.950
0.150
26.730
'.05.040
0.366
15.445
2.217
17.016
2.135
0.398
0.255
0.541
1.579
583.310
194.699
453.863
601.232
194.923
513.717
-------
EMISSIONS (TONS/DAY)
10.jo MONDAY, MAY 3, i939 A-12
NtUi bl
DESCRIPTION
Solvent Metal Cleaning
Printing and Publishing
Fixed Roof Tanks - Crude Oil
Fixed Roof Tanks - Gasoline
Bulk Gas Term.- Subm. .Balanced
Polyethylene Mfg.
Paint and Varnish Mfg.
Automobile. Surf ace Coating
Beverage Can Surface Coating
General Wood Surface Coating
Paper Surface Coating
Misc. Surface Coating
Single Chamber Incinerators
Util. Ext. Comb. - Coal
Util. Ext. Comb. - Oil
Util. Ext. Comb. - Natural Gas
Ind. Ext. Comb. - Other
Comm./Inst. Comb. - Coal
Comm./Inst. Comb. - Oil
Comm./Inst. Comb. - Gas
Comm./Inst. Comb. - Other
Uaste Disposal
Ind. Int. Comb. - Oil Turb.
Ind. Int. Comb. - Oil Recip.
Ind. Int. Comb. - Gas Turb.
Ind. Int. Comb. - Gas Recip.
Util. Int. Comb. - Oil Turb.
Util. Int. Comb. - Oil Recip.
Util. Int. Comb. - Gas Turb.
Cogeneration - Gas Recip.
Cogeneration - Other
Ind. Ext. Comb.- Oi l,>100MM8tu/h
Ind. Ext. Comb.- Gas,>100MMBtu/h
Ind. Ext. Comb.- Gas,<100MMBtu/h
Alt UUI
POO
1
2
4
5
9
24
29
33
34
35
36
37
44
50
51
52
57
58
59
60
61
64
70
71
72
73
74
75
76
81
84
87
88
90
Jt=nassacnus
1985
UN ADJ.
CO
3.725
0.000
0.016
0.000
0.066
0.000
0.013
0.000
O.OCO
0.077
0.000
0.000
0.000
17.885
0.590
6.832
4.787
O.OCO
0.660
0.182
0.088
0.000
5.436
0.016
0.301
0.036
0.080
0.629
0.286
0.785
0.054
0.313
1.469
0.317
0.563
ietcs LAICI.
1985
UNAOJ.
MOX
1.510
0.000
0.000
0.000
'0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
5.085
14.516
77.191
46.069
O.G23
0.785
2.326
0.238
0.001
0.918
0.176
1.440
0.091
0.615
1.660
1.278
1.264
0.431
1.064
15.303
4.216
0.968
]UKT-fUlNI --
1935
UNAOJ.
VOC
22.979
3.314
7.342
0.036
3.851
6.560
0.912
0.023
14.791
5.468
1.280
23.867
25.900
0.173
0.074
1.523
0.082
0.001
0.083
0.044
0.008
0.000
0.353
0.000
0.013
0.001
0.004
0.206
0.072
0.036
0.003
0.005
2.142
1.441
0.145
1985 FULLY
ADJUSTED
CO
3.725
0.000
0.016
0.000
0.066
0.000
0.013
0.000
0.000
0.077
0.000
0.000
0.000
17.885
0.590
6.332
4.787
0.000
0.660
0.182
0.088
0.000
5.436
0.016
0.301
0.036
0.080
0..629
0.286
0.785
0.054
0.313
1.469
0.317
0.563
1985 FULLY
ADJUSTED
NOX
1.510
0.000
0.000
0.000
O.OCO
o.ooc
0.000
o.occ
0.000
0.000
c.cco
0.000
0.000
5.085
14.516
77.191
46.069
O.C23
0.785
2.326
0.238
0.001
0.918
0.176
1.440
0.091
0.615
1 .660
1.278
1.264
0.431
1.064
15.303
4.216
0.968
1985 FULLY
ADJUSTED
VCC
22.979
3.314
7.342
0.036
3.351
6.560
0.912
0.022
14.791
5.468
1.280
23.867
25.900
0.173
0.074
1.528
0.082
0.001
0.083
0.044
0.008
0.000
0.353
0.000
0.013
0.001
0.004
0.206
0.072
0.036
0.003
0.005
2.142
1.441
0.145
45.206
177.216
123.239
45.206
177.216
123.239
-------
EMISSIONS (TGNS/uAY)
'.G.56 MONDAY, HAY 3, i939 A-i3
- 4£DS STATE COOE=Massacnusetts CAi EGORY=M08ILc --•
1985 1985 1935
JE3CRIPTJOH
......... ............. . NEDS S
DESCRIPTION
Res. Fuel - Anth. Coal
Res. Fuel • Sit. Coal
Res. Fuel - Dist. Oi I
Res. Fuel - Natural Gas
Res. Fuel - Wood
Comm/Inst. Fuel - Anth. Coal
Comm/Inst. Fuel - Oist. Oil
Comm/Inst. Fuel • Resid. Oil
Comm/Inst. Fuel - Natural Gas
Ind. Fuel - Sit. Coal
Ind. Fuel - Coke
Ind. Fuel - Oist. Oil
Ind. Fuel - Residual Oil
Ind. Fuel - Natural Gas
Incineration - Residential
Incineration - Industrial
Incineration - Comm/Inst.
Open Burning - Residential
Open Burning • Industrial
Open Burning - Comm/Inst.
Off -Highway Gas Vehicles
Off -Highway Diesel Vehicles
Railroad Locomotives
Aircraft • Military
Aircraft - Civil
Aircraft - Commercial
Vessels - Diesel
Vessels - Residual Oil
Vessels - Gasoline
Gasoline Marketed
Structural Fires
Degreasing
0 rye lean ing
Graphic Arts/Printing
Architectural Coating
Auto Body Repair
Moto Vehicla Mfg.
Fab.-icatsd Petals
Machinery Mfg.
'urni ture Mfg.
Flat '-.'ocd Products
sec
UNAOJ .
CO
ALL 1735.510
TATE COOE=MassachuseC ts
1985
UNADJ.
sec
1
2
3
5
6
7
9
10
11
14
15
16
17
18
21
22
23
24
25
26
39
44
45
46
47
48
50
51
52
54
64
78
79
80
82
83
24
S6
87
88
39
CO
0.326
0.000
0.422
0.225
30.259
0.027
1.030
0.447
0.668
0.971
0.051 *
0.050
0.903
2.085
103.199
0.082
1.567
43.826
0.424
0.035
362.201
2.719
9.450
3.039
23.432
21.116
1.415
0.003
32.737
0.000
19.032
0.000
0.000
0.000
0.000
0.000
o.ono
0.000
0.000
0.000
0.000
UNACJ.
NOX
392.400
i985
UNAOJ.
•iCX
0.010
0.000
1.518
1.127
0.363
0.444
4.120
4.921
3.338
7.537
0.101
0.211
9.933
10.346
0.382
0.012
0.542
2.620
0.023
0.002
12.668
8.933
26.896
0.645
0.450
7.732
4.043
0.101
0.418
0.000
0.441
0.000
O.GOO
0.000
0.000
0.000
0.000
0.000
0.000
o.ooc
O.COO
bNACj.
voc
407.670
p*^ov — unuupo 1 1 c
uUKT -NUNMUo 1 LC
1985
UNADJ.
voc
0.036
0.000
0.115
0.000
6.586
0.003
0.120
0.151
0 . 335
0.027
0.000
0.014
0.083
0.109
6.742
0.011
0.130
13.815
0.121
0.012
41.282
1.452
6.532
1.614
1.308
5.988
1.011
0.009
9.184
61.413
3.499
51.807
25.416
26.901
40.146
15.653
0.403
9.441
6.671
6.321
0.331
1935 FULLY
~OJUS"j
CO
2358.520
1985 FULLY
ADJUSTED
CO
0.326
0.000
0.422
0.225
30.259
0.027
-.330
0.447
O.£o3
0.971
0.051
0.050
0.903
2.085
103.199
0.082
1.567
43.826
0.424
0.035
362.201
2.719
9.450
3.039
23.432
21.116
1.415
0.003
55.652
O.COO
19.032
0.000
0.000
0.000
0.000
0.000
0 . COO
0.000
0.000
0.000
O.uOO
1985 FULLY
ADJUSTED
NOX
316.217
1935 FULLY
ADJUSTED
NOX
0.011
o.ono
1.518
1.127
0.363
0.444
4.i:o
4.921
3.233
7.537
0.101
0.211
9.933
10.346
0.382
0.012
0.542
2.620
0.023
0.002
12.668
3.933
26.396
0.645
0.450
7.732
4.043
0.101
0.710
C.OOO
0.441
0.000
O.COO
0.000
0.000
0.000
O.COO
0.000
0.000
0.000
o.ooc
1985 FULLY
ADJUSTED
VOC
583.314
!985 FULLY
ADJUSTED
VOC
0.036
0.000
0.115
0.000
6.586
0.003
0.120
0.151
1. "35
0.027
0.000
0.014
0.083
0.109
6.742
0.011
0.130
13.815
0.121
0.012
41.282
1.452
6.532
1.614
1.308
5.988
1.011
0.009
15.613
90.392
3.499
51.807
c5.-,;s
26.901
80.291
15.653
? . -03
?! 441
6.671
6.321
0.63-
-------
EMISSIONS (TONS/DAT)
10.00 MONDAY, MAY 3, 1939
DESCRIPTION
Other Trans. Equip. Mfg.
Electrcal Equip. Mfg.
Ship Building and Repair
Misc. Ind. Mfg.
Misc. Ire. Solvent Use
FOTUs
Cutback Asphalt Paving Oper.
Fugitives from SCCM!
Sulk Terminals and Sulk Plants
Process Ems. • Bakeries
Process Ems. - Pharn. Mfg.
Proc. cms.- Synth. Fibers Mfg.
Crude Oil/Nat.Gas Prod. Fields
Hazardous Waste TSDFs
. COD
sec
90
91
92
93
95
100
101
102
103
105
106
107
108
109
E=Massacnuseti
1985
UNAOJ.
CO
0.000
0.000
0.000
0.000
o.ooo
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
:s UAitui
1985
UNAOJ.
NOX
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
o.oco
0.000
0.000
0.000
JKT=NUNHUBILt
1585
UNADj.
VCC
0.208
1.863
0.817
77.722
168.455
1.303
7.816
3.733
15.474
3.659
C.?92
0.010
0.121
2.161
1985 FULLY
ADJUSTED
CO
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
1985 FULLY
ADJUSTED
NOX
0.000
0.000
0.000
0.000
O.OCQ
o.oco
0.000
o.oco
0.000
0.000
o.occ
0.000
0.000
0.000
1985 FULL?
ADJUSTED
VOC
0.210
1.36C
0.820
77.720
1 59. 970
1.302
7. Sic
3. 733
23.521
• 3.659
o.?9:
0.010
0.121
2.593
661.745
109.389
735.11C
-------
EMISSIONS ^TONS/DAY)
10.36 MONDAY. MAY 3, 1939
- NCU5
DESCRIPTION
Solvent Metal Cleaning
Fixed Roof Tanks - Crude Oil
Fixed Roof Tanks - Gasoline
£FS TanKS - Crude Ji I
EFR Tarxs - Gasoline
3ulk '"as r^rni.- Nor vitanced
'etr. ^arinerv WU Treatment
Ptr. Refinery Vacuun Oistil.
Paint and Varnish Mfg.
Misc. surface Coating
Coke Oven Byproduct Plants
Iron/Steel Blast Furn. .Sinter.
Single Chamber Incinerators
Util. Ext. Comb. - Coal
Util. ~xt. Comb. - Matural Gas
ind. Ext. Comb. - Otner
Comm./Inst. Comb. - Coal
Comm./Inst. Comb. - Oil
Comm./inst. Comb. - Gas
Comm./Inst. Comb. - Other
Internal Comb. - Aircraft
Waste Disposal
Ind. Int. Comb. • Oil Recip.
Ind. Int. Comb. - Gas Recip.
Util. Int. Comb. - Gas Recip.
Cogeneraticn - Other
Ind. Ext. Comb.- Oi l,>100MMBtu/h
Ind. Ext. Comb.- Gas,>100MMBtu/h
Ind. Ext. Comb.- Gas,<100MMBtu/h
SIMI C
POO
1
4
$
6
7
iO
26
27
29
37
39
41
44
SO
51
52
57
58
59
60
61
63
64
71
73
77
34
87
88
90
Luue=mcn ig;
1985
UNADJ.
CO
166.900
0.791
0.000
0.000
0.000
0.000
0.000
0.000
66.872
0.000
O.OCC
4.152
67.611
0.001
17.915
0.190
0.471
0.069
0.644
0.026
0.235
0.000
142.295
15.521
0.000
3.500
0.286
5.553
0.278
0.292
0.310
an UM i cuu
1935
UNAOJ.
NGX
19.194
0.093
0.000
0.000
Q ")np
0.000
c.occ
0.000
1.-43
0.000
o.ccc
2.029
0.000
0.008
545.397
2.323
7.233
0.934
6.236
0.308
1.591
0.000
3.684
2.346
0.003
27.852
2.541
41 261
2.322
4.338
10.046
K I =rU( N 1 - - - - -
1935
UNAOJ.
VQC
60.464
15.115
3.546
4.850
:.032
1.940
2.C20
1.031
7.203
5.349
134.488
7.048
0.000
0.000
2.166
0.054
0.009
0.004
0.034
0.001
0.003
0.000
5.389
0.793
0.000
0.296
0.022
0.163
0.026
0.005
0.017
1985 FULLY
ADJUSTED
CO
166.900
0.791
0.000
0.000
C.COO
0.000
o.coo
0.000
66.372
0.000
0.000
4.152
67.611
0.001
17.915
0.190
0.471
0.069
0.644
0.026
0.235
0.000
142.295
15.521
0.000
3.500
0.286
5.558
0.278
0.292
0.310
1935 FULLY
ADJUSTED
NCX
19.194
0.093
0.000
0.000
0.000
0.000
o.cco
0.000
1.445
0.000
j.OOO
2.029
0.000
0.008
545.397
2.323
7.233
C. r34
6.236
0.308
1.591
0.000
3.684
2.346
0.003
27.852
2.541
41.261
2.322
4.338
10.046
1935 FULLY
ADJUSTED
VOC
60.464
15.115
3.546
4.350
1.032
1.94C
2.020
1.031
7.203
5.349
134.4S8
7.043
0.000
0.000
2.166
0.054
0.009
0.004
0.034
0.001
0.003
0.000
5.389
0.793
0.000
0.296
0.022
0.163
0.026
0.005
0.017
493.915
681.136
253.069
493.915
681.186
253.069
-------
EMISSIONS (TONS/DAY)
NEDS STATE COOE=Michigan
10.36 MONDAY, MAY 3, i939 A-26
DESCRIPTION
_ ucncc
DESCRIPTION
Res. Fuel - Anth. Coal
Res. Fuei. - Dist. Oil
Res. "uel - Natural Gas
Res. Fuel - Wood
Comm/Inst. Fuel - Anth. Coal
Comm/Inst. Fuel - Dist. Oil
Coimi/Ir.st. Fuel - Sesid. Oil
Comm/Inst. Fuel - Natural Gas
Ind. ruei - Dist. Oil
Ind. Fuel - Residual Oil
Ind. Fuel - Natural Gas
Incineration - Residential
Incineration - Industrial
Incineration - Comm/Inst.
Open Burning - Residential
Open Burning - Industrial
Open Burning - Comm/Inst.
Off -Highway Gas Vehicles
Off-Highway Diesel Vehicles
Railroad Locomotives
Aircraft - Military
Aircraft - Civil
Aircraft - Commercial
Vessels - Diesel
Vessels - Residual Oil
Vessels - Gasoline
Gasoline Marketed
• Forest Ui Idf ires
Managed Burning - Prescribed
Structural Fires
Degreasing
D rye lean ing
Graphic Arts/Printing
Rubber and Plastic Mfg.
Arcnitect'jral Coating
Auto Body Repair
Moto Vehicle Mfg.
Paper Coating
.•ucncstsc .-ietais
Machinery '*fg.
Furni ture Mfg.
Flat Wood Products
Other Trans. Equip. Mfg.
1935
UNADJ.
SCC CO
ALL 2958.980
TATE COOE=Michigan
SCC
1
3
5
6
7
9
10
11
16
17
18
21
22
23
24
25
26
39
44
45
46
47
48
50
51
52
54
60
61
64
78
79
30
31
o2
83
84
35
37
88
39
90
I985
•JNAD J .
CO
0.005
0.101
0.736
33.837
0.005
0.358
0.040
1.944
0.660
0.187
10.853
149.389
0.159
3.362
91.024
0.752
0.339
483.318
12.i11
5.493
0.334
31.948
15.066
0.220
0.000
23.542
0.000
0.974
0.000
14.612
0.000
0.000
0.000
0.000
•j . uuG
0.000
0.000
0.000
c.ooo
0.000
0.000
0.000
LAI tljU
1985
UNADJ.
NOX
KT=MUBlLt
1985
UNADJ.
voc
488.100 564.780
CATcGURY-NuNMUo 1 Li
1985 1985
UNADJ. UNADJ.
NOX
0.000
0.363
3.681
0.406
0.077
1.431
0.439
9.719
2.784
2.063
61.192
0.553
0.023
1.163
5.441
0.041
0.023
16.904
40.772
15.634
0.071
0.614
5.517
0.628
0.008
0.300
0.000
0.027
0.000
0.338
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
. . _ ^ 0
0.000
0.000
0.000
0.000
VOC
0.001
0.023
0.000
7.365
0.001
0.042
0.013
0.246
0.134
0.017
0.675
9.760
0.021
0.279
28.692
0.215
0.120
55.087
6.629
3.797
0.177
1.784
4.272
0.157
0.001
6.604
76.131
0.133
0.000
2.686
64.874
26.597
12.750
45.153
»5. i99
18.569
27.531
9.673
< -j . • _i^
3.417
2.605
0.721
0.011
1985 FULLY
ADJUSTED
CO
3067.980
1985 FULLY
ADJUSTED
CO
0.005
0.101
0.736
33.837
0.005
0.358
0.040
1.944
0.660
0.187
10.853
149.389
0.159
3.362
91.024
0.752
0.339
483.318
12.411
5.493
0.334
31.948
15.066
0.220
0.000
47.083
0.000
0.974
0.000
14.612
0.000
0.000
0.000
0.000
•J.OUO
0.000
0.000
0.000
- . W.OU
0.000
0.000
0.000
0.000
1985 FULLY
ADJUSTED
NOX
387.704
1985 FULLY
ADJUSTED
NOX
0.000
0.363
3.681
0.406
0.077
1.431
0.439
9.719
2.73-
2.063
61.192
0.553
0.023
1.163
5.441
0.041
0.023
16.904
40.772
15.634
0.071
0.614
5.517
0.628
0.008
0.601
0.000
0.027
0.000
0.338
0.000
0.000
0.000
0.000
0.-OG
0.000
0.000
o.occ
, , ..^3
0 . OCO
0.000
0.000
0.000
1985 FULLY
ADJUSTED
VCC
724.970
1985 FULLY
ADJUSTED
VOC
0.001
0.023
0.000
7.365
0.001
0.042
0.013
0.246
0.134
0.017
0.675
9.760
0.021
0.279
28.692
0.215
0.120
55.087
6.629
3.797
0.177
1.784
4.272
0.157
0.001
13.209
130.946
0.133
0.000
2.686
64.874
26.597
12.750
45.153
70.J57
18.569
27.531
9.678
J . . •_ —
3.417
2.605
0.721
0.011
-------
HM!SSIC:
-------
EMISSIONS (TONS/DAY)
10.36 MONDAY, MAY 3, 1989
NfcUS S!
DESCRIPTION
Solvent Metal Cleaning
Fixed Roof Tanks - Crude Oil
Rubber T'"rs Mfg.
Automobile Surface Ccating
Beverage Can Surface Coating
Paper Surface Coating
Misc. Surface Coating
Pulp/Paper - Recovery Furnace
Util. Ext. Comb. - Coal
Util. ext. Comb. - Oil
Util. Ext. Comb. - Other
Ind. Ext. Comb. - Other
Comm./Inst. Comb. - Oil
Comm./Inst. Comb. - Gas
Waste Disposal
Util. Int. Comb. - Oil Turb.
Util. Int. Comb. - Gas Turb.
Ind. Ext. Comb.- Oi l,<100MMBtu/h
Ind. Ext. Comb.- Oi l,>100MMBtu/h
Ind. Ext. Comb.- Gas,>100MMBtu/h
I nd. Ext . Comb. -Cogenerat i on
Ind. Ext. Comb.- Gas,<100MMBtu/h
fATE CO
POO
1
4
30
33
34
36
37
42
50
51
53
57
59
60
64
74
76
85
87
88
89
90
ot=New Hamp
1985
UNADJ.
CO
6.746
0.000
0.000
0.000
0.000
0.000
0.000
0.000
5.234
0.095
0.772
0.159
0.000
0.046
6.555
0.000
0.000
o.oco
0.007
10.185
0.034
0.048
8.136
snire CAICI
1985
UNADJ.
NOX
0.375
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.024
44.155
8.367
0.321
0.000
0.126
0.160
0.219
0.019
0.005
0.073
^ 4.006
0.162
0.215
0.348
)UKT=r1UlNI -•
1935
UNAOJ.
voc
5.480
0.508
0.255
0.060
3.360
0.262
0.570
0.217
0.000
0.827
0.244
0.005
0.000
0.000
0.077
0.000
0.000
0.000
0.007
1.273
0.000
0.000
0.340
1985 FULLY
ADJUSTED
CO
6.746
0.000
0.000
0.000
C.COO
0.000
0.000
0.000
5.234
0.095
0.772
0.159
0.000
0.046
6.555
0.000
0.000
0.000
0.007
10.185
0.034
0.048
8.136
1985 FULLY
ADJUSTED
NOX
0.375
0.000
0.000
0.000
O.OCO
0.000
0.000
0.000
0.024
44.155
8.367
0.321
0.000
0.126
0.160
0.219
0.019
0.003
0.073
4.006
0.162
0.215
0.348
1985 FULLY
ADJUSTED
VOC
5.480
0.303
0.255
0.060
3.360
0.262
0.570
0.217
O.uOO
0.827
0.244
0.005
0.000
0.000
0.077
0.000
0.000
0.000
0.007
1.273
0.000
0.000
0.340
38.017
58.580
13.492
38.017
58.580
13.492
-------
EMISSIONS (TGHS/OAi)
10.56 MONDAY, f.A't 5, 1989 A-29
NEDS SI
DESCRIPTION
Art coo
sec
fc=New Hampsnire
1985
UNADJ.
CO
ALL 356.270
1985
UNADJ.
3E3C2IPTION
Res. Fuel - Anth. Coal
Res. reel - Dist. C;'l
Res. Fuel - Natural Gas
Res. Fuel - Wood
Comm/Inst. Fuel - Anth. Coal
Comm/Inst. Fuel - Dist. Oil
Comm/insc. r'uel - Natural Gas
Ind. Fuel - Anth. Coal
ina. rue i • oit. Coal
Ind. Fuel - Coke
Ind. Fuel - Dist. Oil
Ind. Fuel - Natural Gas
Incineration - Residential
Incineration - Industrial
Incineration - Comm/Inst.
Open Burning - Residential
Open Burning - Comm/Inst.
Off -Highway Gas Vehicles
Off-Highway Diesel Vehicles
Railroad Locomotives
Aircraft - Military
Aircraft - Civil
Aircraft - Commercial
Vessels - Diesel
Vessels - Gasoline
Gasoline Marketed
Forest Ui Idf ires
Structural Fires
Degreasing
0 rye lean ing
Graphic Arts/Printing
Rubber and Plastic Mfg.
Architectural Coating
Auto Body Repair
iioio «srnci3 iirg.
Paper Coating
Fabricated Metals
Machinery Mfg.
cLst Weed ."••cducts
Other Trans. Equip. Mfg.
Electrcal Equip. Mfg.
Misc. Ind. Mfg.
3CC
1
3
5
6
7
9
11
•13
14
15
16
18
21
22
23
24
26
39
44
45
46
47
48
50
52
54
60
64
78
79
80
81
32
83
'J**
85
86
37
39
90
91
93
CO
0.018
0.125
0.029
17.957
0.004
0.109
0.083
0.002
0.022
0.009 k
0.060 *
0.444
13.378
0.029
0.409
16.053
0.023
98.664
2.107
0.065
1.477
7.965
1.530
0.014
1.518
0.000
0.025
2.467
0.000
0.000
0.000
0.000
0.000
0.000
u • w C C
0.000
0.000
0.000
0.000
0.000
0.000
o.oco
LA
1985
UNADJ.
NOX
70.440
C * T
1985
UNAOJ .
NOX
O.OC1
0.^51
0. 142
0.215
0.058
0.435
0.413
0.042
0.173
0.017
0.253
3.267
0.049
0.004
0.141
0.959
0.001
3.450
6.921
0.185
0.313
0.153
0.560
0.040
0.019
0.000
0.000
0.057
0.000
0.000
0.000
0.000
0.000
0.000
• • -"
0.000
0.000
C.CGO
0.000
0.000
0.000
0.000
1 ttjUKT=MUBlLt
1935
UNADJ .
VOC
75.480
PfO-0 V — kinUMf"lQ T 1 C
CuUK T — NUNPlUo 1 LC
1985
UNADJ.
VOC
0.002
0.034
0.000
3.908
0.000
0.012
0.010
0.000
O.QOO
0.000
0.016
0.038
0.874
0.003
0.033
5.060
0.008
11.245
1.1 ?.5
0.045
0.784
0.444
0.433
0.010
0.425
11.544
0.003
0.453
8.872
3.452
3.805
15.926
6.576
4.126
,
6.668
1.175
1.435
0.383
0.022
0.398
12.865
1985 FULLY
ADJUSTED
CO
384.150
1985 FULLY
ADJUSTED
CO
0.018
0.125
0.029
17.957
0.004
0.109
O.OS3
0.002
0.022
0.009
0.060
0.444
13.378
0.029
0.409
16.053
0.023
98.664
2.107
0.065
1.477
7.965
' 1.530
0.014
3.036
0.000
0.025
2.467
0.000
0.000
0.000
0.000
O.GOO
0.000
0.000
0.000
o.coo
0.000
o.oco
c.ooo
0.000
5985 FULLY
ADJUSTED
NOX
56.201
1985 FULLY
ADJUSTED
NOX
0.001
0.451
0.142
0.215
0.058
0.435
0.413
0.042
0.173
0.017
0.253
3.267
0.049
0.004
0.141
0.959
0.001
3.450
6.921
0.185
0.313
0.153
0.560
0.040
0.038
0.000
0.000
0.057
O.COO
0.000
0.000
0.000
0.000
0.000
0.000
0.000
o . :co
0.000
0.000
c.oco
0.000
1985 FULLY
ADJUSTED
VOC
98.430
•,=85 FULLY
ADJUSTED
VOC
0.002
0.034
0.000
3.908
0.000
0.012
0.010
0.000
o.ccc
0.000
0.016
0.033
0.874
0.003
0.033
5.060
0.008
11.245
1.125
•0.045
0.784
0.444
0.433
0.010
0.351
19.071
0.003
0.453
8.872
3.452
3.805
15.926
16.30;
4.1?6
-
6.668
1.175
',.435
0.383
0.022
0.398
12.365
-------
frilSSIONS (TONS/DAY)
;G.3b MONDAY, ,MAY 3, 1929
NEDS STATE
DESCRIPTION
Misc. Ind. Solvent Use
POTWs
Cutback Asphalt Paving Oper.
Fugitives from SOCMI
Bulk Terminals and 3ulk Plants
Process E.ns. - Bakeries
Process Eins. - Pharm. Mfg.
Crude Oil/Hat.Gas .'rod. Fields
Hazardous '.'aste TSDfs
; CODE =
sec
95
100
101
102
103
105
106
108
109
=New Hampsnir
1985
UNAOJ.
CO
0.000
0.000
0.000
0.000
n.coo
0.000
0.000
0.000
0.000
•e UAituu>
1985
UNAOJ.
NOX
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
-------
EMISSIONS 100MMBtu/h
Ind. Hxt. Comb.- Gas,>100MMBtu/h
Ind. Ext. Comb.- Gas,<100MMBtu/h
)IAIt U
POD
1
2
3
4
5
6
7
11
19
20
21
23
24
25
26
27
29
30
33
34
35
36
37
43
50
51
52
57
59
60
63
64
71
72
74
75
76
84
85
87
38
90
JUt=New jer
1985
UNADj.
CO
7.871
0.000
0.000
0.000
0.000
0.038
0.000
0.000
0.000
0.000
0.005
O.COO
0.000
0.003
0.000
0.000
0.736
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
4.673
4.311
0.000
3.602
0.268
0.000
0.013
0.250
0.121
1.690
1.926
0.000
0.691
0.192
1.030
0.919
0.484
0.291
sey LAICUU
1985
UNADJ.
NOX
35.595
0.000
0.003
O.COO
0.000
0.000
0.000
o.ooo.
O.COO
O.COO
0.066
0.000
0.005
12.607
0.000
0.000
0.549
0.000
0.000
* 0.000
0.014
0.000
0.000
0.000
0.000
137.934
77.101
0.002
0.301
1.893
0.005
0.105
1.264
7.038
31.016
7.526
0.023
2.579
1.582
16.041
10.270
6.472
3.566
KT=KU1NI
1985
UNADo.
VOC
45.771
0.063
6.915 .
0.000
1.901
10.098
1.298
7.791
1.168
1.433
0.072
0.033
0.223
0.412
0.086
3.871
0.380
0.198
0.058
5.145
7.202
2.793
0.033
12.011
1.113
0.853
0.752
0.000
0.983
0.005
0.000
0.000
0.002
0.000
0.214
0.637
0.000
0.077
0.008
0.026
0.067
0.045
0.023
1985 F'JLLf
ADJUSTED
CO
7.871
0.000
0.000
0.000
0.000
0.038
0.000
0.000
0.000
0.000
0.005
0.000
0.000
0.003
0.000
o.ooc
0.736
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
4.673
4.311
0.000
3.602
0.268
0.000
0.013
0.250
0.121
1.690
1.926
0.000
0.691
0.192
1.030
0.919
O.i34
0.291
1985 .-'ULL'.'
AG^uSTcD
NOX
35.595
0.000
0.003
O.COO
o.:no
0.000
0.000
o.:oo
o.eoo
C.-JOO
0.066
0.000
0.005
12.607
0.000
O.GCO
0.549
c.:cc
0.000
0.000
0.014
0.000
0.000
0.000
0.000
137.934
•77.101
0.002
0.301
1.893
0.005
0.105
1.264
7.038
31.016
7.526
0.023
2.379
1.532
16.041
10.270
6. i~2
3.546
•?c5 .-L'LLY
nJuUSTEC
VOC
45.771
0.063
6.915
G.CCO
'.901
10.098
1 . 293
".;?•;
! .163
1.438
0.072
0.033
0.223
0.412
0.086
- T7-
0.330
:.:"3
0 . 053
5.145
7.202
2.793
0.033
12.011
1.113
0.853
0.752
0.000
0.983
0.005
0.000
0.000
0.002
0.300
0.214
0.637
0.000
0.077
C.CC3
0.026
0.067
J . j4;
0.023
29.115
353.561
113.765
29.115
353.561
113.765
-------
EMISSIONS ^TONS/DAY)
NEDS STATE CODE=New Jersey
i O.jo .1GNOAY, MAf 0,
DESCRIPTION
DESCRIPTION
Res. Fuel - Anth. Coal
Res. Fuel - Bit. Coal
Res. Fuel - Dist. Oil
Res. Fuel - Natural Gas
Res. Fuel - Wood
Comm/Inst. Fuel - Anth. Coal
Comm/Inst. Fuel - Sit. Coal
Comm/Inst. Fuel - Dist. Oil
Comm/Inst. Fuel - Resid. Oil
Comm/Inst. Fuel - Natural Gas
Ind. Fuel - Bit. Coal
Ind. Fuel - Oist. Oil
Ind. Fuel - Natural Gas
Incineration - Residential
Incineration - Industrial
Incineration - Comm/Inst.
Open Burning - Residential
Off-Highway Gas Vehicles
Off -Highway Diesel Vehicles
Railroad Locomotives
Aircraft - Military
Aircraft - Civil
Aircraft - Commercial
Vessels - Diesel
Vessels - Residual Oil
Vessels - Gasoline
Gasoline Marketed
Managed Burning - Prescribed
Structural Fires
Degreasing
D rye lean ing
Graphic Arts/Printing
Rubber and Plastic Mfg.
Architectural Coating
AUCO a cay .\epair
Moto Vehicle Mfg.
Paper Coating
Fabricated Metals
Furniture Mfg.
Flat Wood Products
Other Trans. Equip. Mfg.
Electrcal Equip. Mfg.
1985
UNADJ.
SCC CO
ALL 2408.560
ATE COOE=Neu Jersay
3CC
1
2
3
5
6
7
8
9
10
11
14
16
18
21
22
23
24
39
44
45
46
47
48
50
51
52
54
61
64
78
79
80
31
82
T7
84
85
86
88
89
90
91
1985
UNADJ.
CO
0.156
0.093
0.620
0.495
49.223
0.087
0.026
1.041
0.330
1.427
1.589
0.842
2.172
29.752
0.241
19.951
39.605
424.898
7.333
9.741
4.522
35.239
15.853
4.458
0.158
27.585
0.000
0.000
24.057
0.000
0.000
0.000
0.000
0.000
:.:;:o
0.000
0.000
0.000
0.000
0.000
0.000
0.000
UAI tUt
1985
UN ADJ.
NOX
JKT=MUblLi
1985
UNADj.
VOC
577.580 601.070
P ft TCPPlD V — LJOUMAQ TIC -
CM 1 CuUK T -NUNHUo 1 L t
1985 1985
UNADJ. UNADJ.
NOX
0.005
0.003
2.230
2.473
0.591
1.421
0.044
4.162
3.526
7.136
12.330
3.553
8.690
0.110
0.035
6.906
2.367
14.860
24.253
27.723
0.961
0.677
5.805
12.738
4.716
0.352
0.000
0.000
0.558
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
voc
0.017
0.010
0.169
0.000
10.714
0.010
0.002
0.122
0.111
0.181
0.044
0.234
0.083
1.944
0.032
1.654
12.484
48.428
3.943
6.733
2.401
1.968
4.495
3.185
0.433
7.739
83.944
0.000
4.423
40.345
30.067
31.547
30.052
52.157
1.473
45.455
3.964
10.423
1.013
0.085
1.669
1933 rULLY
AC.U37ED
CO
3866.110
1985 FULLY
ADJUSTHO
:o
J.156
0.093
0.620
0.495
49.223
0.087
0.026
1.041
0.330
1.427
1.539
0.842
2.172
29.752
0.241
19.951
39.605
'424.398
7.383
9.741
4.522
35.239
15.353
4.458
0.158
46.894
0.000
0.000
24.057
O.CCO
0.000
0.000
0.000
0.000
0.000
0.000
0.300
0.000
0.000
o.coo
0 . 000
!?85 FULLY
ADJUSTS:
NOX
473.667
•'•'85 FULLY
ADJUSTED
MOX
0.005
0.003
2.230
2.473
0.591
1.421
v.~44
4.162
T '."A
7.136
12.330
3.253
8.690
0.110
0.035
6.906
2.367
14.860
24.253
27.723
0.961
0.677
5.305
12.738
4.716
0.598
0.000
0.000
0.558
O.COO
0.000
0.000
C.CQO
0.000
0.000
0.000
r:°?
'i. 000
0.000
0.000
•J.OUO
-,9S5 -LILLY
.AD.t'STHD
VOC
885.176
'985 FULLY
40 JUS TED
VOC
0.017
O.C10
0.169
0.000
10.714
0.010
C.C02
0.122
0 . ! ' '
0.131
0.044
0.234
0.083
1.944
0.032
1.654
12.434
48.428
3.943
6.733
2.401
1.968
4.4=5
3.133
0.433
13.156
126.924
0.000
4.423
40.345
30.067
31.547
30. 032
88.667
1.473
45.455
2.764
-0.-73
1.013
0.035
i .oc9
-------
EMISSIONS
-------
5MIS3IONS (fONS/OAY)
10.35 MONDAY, ;1AY 3,
NEDS
DESCRIPTION
Solvent Metal Cleaning
Printing and Publishing
EFR Tanks - Gasoline
Terephthalic Acid Mfg.
Polyethylene Mfg.
Ethylene Mfg.
Paint and Varnish Mfg.
Automobile Surface Coating
Beverage Can Surface Coating
Paper Surface Coating
Misc. Surface Coating
Coke Oven Byproduct Plants
Pulp/Paper - Recovery Furnace
Single Chamber Incinerators
"Jtil. Ext. Comb. - Coal
Util. Ext. Comb. - Oil
Util. Ext. Comb. - Natural Gas
Ind. Ext. Comb. - Other
Comm./Inst. Comb. - Coal
Comm./Inst. Comb. - Oil
Comm./Inst. Comb. - Gas
Waste Disposal
Cogeneration - Other
Ind. Ext. Comb.- Oi I ,>100MMBtu/h
Ind. Ext. Comb.- Gas,>100MMBtu/h
Ind. Ext. Comb.- Gas,<100MMBtu/h
STATE CODE=New York CATEGORY=POINr
POD
1
2
7
17
24
25
29
33
34
36
37
39
42
44
50
51
52
57
58
59
60
64
84
87
88
90
1985
1 1 It A p) I
UnMU J .
CO
75.952
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
4.044
9.197
13.370
3.103
0.000
0.213
1.473
0.480
7.504
2.408
2.216
1.982
2.064
1985
i luin i
UN AUd •
NOX
35.630
0.000
0.000
0.000
0.000
0.011
0.000
0.000
0.003
0.000
0.000
0.000
4.272
0.995
6.639
158.677
115.668
106.724
3.436
* 1.859
15.061
4.657
1.969
45.497
33.085
4.948
7.016
1985
UNAD J .
VOC
92.469
0.246
6.345
5.992
0.019
7.135
0.051
0.261
9.306
0.974
4.085
8.060
0.047
0.000
0.555
2.586
4.291
0.253
0.000
0.059
1.313
0.064
0.222
0.731
6.357
0.412
3.156
19S5 FULLY
AD wLJSTED
CO
75.952
0.000
0.000
0.000
n.ooo
o.coo
D.OOO
0.000
3.:oo
J.OOO
O.QOO
0.000
0.000
0.000
4.044
7.197
13.370
5..:c2
0.000
0.213
1.473
0.480
7.504
2.408
2.216
1.982
2.064
1985 FULLY
AD JUSTc J
NOX
35.630
0.000
0.000
0.000
o.oon
o.oi-
o.oco
0.100
C.O'JZ
o.oco
0.000
0.000
4.272
0.995
6.639
158.577
115.668
106. 774
3.436
1.859
15.061
4.657
1.969
45.497
33.085
4.948
7.016
1985 FULLf
ADJL'jT'i-"
vcc
92.469
0.246
6.345
5.992
0.01?
7.123
C.CS1
0.261
9.306
0.974
4.085
8.060
0.047
0.000
0.555
2.586
4.291
0.253
0.000
0.059
1.313
0.064
0.222
0.731
6.357
0.412
3.156
129.006
546.147
154.989
129.006
546.147
154.989
-------
EMISSIONS (TONS/DAY)
!u.56 MONDAY, MAY 5, 1539
DESCRIPTION
ucnc c
DESCRIPTION
Res. F'jel - Anth. Coal
Res. Fuel - Bit. Coal
Res. Fuel - Dist. Oil
Res. Fuel - Natural Gas
Res. Fuel - Wood
Comm/Inst. Fuel - Anth. Coal
Comm/Inst. Fuel - Bit. Coal
Comm/Inst. Fuel - Dist. Oil
Comm/Inst. Fuel - Resid. Oil
Ccmn/tnst. Fuel - Natural Gas
Ind. Fuel - Anth. Coal
Ind. Fuel - Bit. Coal
Ind. Fuel - Dist. Oil
Ind. Fuel - Natural Gas
Incineration - Residential
Incineration - Industrial
Incineration - Comm/Inst.
Open Burning - Residential
Open Burning - Industrial
Open Burning - Comm/tnst.
Off -Highway Gas Vehicles
Off-Highway Diesel Vehicles
Railroad Locomotives
Aircraft - Military
Aircraft - Civil
Aircraft - Commercial
Vessels - Diesel
Vessels - Residual Oil
Vessels - Gasoline
Gasoline Marketed
Structural Fires
Degrees ing
D rye lean ing
Graphic Arts/Printing
Pubber and Plastic Mfg.
Auto Body Repair
Moto Vehicle Mfg.
Paper Coating
Machinery Mfg.
Furniture Mfg.
Flat Wood Products
1985
UNADJ.
SCC CO
ALL 4207.350
TATE COOE=New York
SCC
1
2
3
5
6
7
8
9
10
11
13
14
16
18
21
22
23
24
25
26
39
44
45
46
47
43
50
51
52
54
64
78
79
30
81
83
84
35
87
88
89
1985
UNADJ .
CO
0.558
0.798
1.126
1.105
135.147
0.122
0.220
2.326
1.599
2.440
0.001
1.302
0.570
7.165
69.718
0.496
7.894
130.771
4.405
0.525
848.804
14.141
7.807
6.391
50.234
39.629
0.421
0.010
58.305
0.000
60.125
0.000
0.000
0.000
0.000
0.000
0.000
o.oco
0.000
0.000
0.000
CAIfcljUK
1985
UNADJ.
NOX
1012.430
CATEGORY=
1985
UNADJ.
NOX
0.018
0.026
4.052
5.525
1.624
1.996
0.370
9.302
17.591
12.201
0.033
' 10.107
2.406
38.259
0.258
0.073
2.732
7.817
0.243
0.037
29.687
46.456
22.219
1.358
0.965
14.512
1.203
0.300
0.744
0.000
1.394
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
T=MOBlLt
1985
UNADJ.
VOC
1089.260
NONMOB I LE - - •
1985
UNADJ.
VOC
0.062
0.089
0.307
0.000
29.416
0.014
0.017
0.272
0.540
0.309
0.000
0.036
0.158
0.414
4.555
0.065
0.655
41.221
1.256
0.185
96.743
7.553
5.396
3.394
2.805
11.237
0.301
0.028
16.357
151.867
11.054
88.182
61.231
73.657
66.269
37.983
4.749
61.495
10.165
19.730
2.067
1985 FULLY
ADJUSTED
CO
6144.860
1985 FULLY
ADJUSTED
. CO
0.558
0.798
1.126
1.105
135.147
0.122
0.220
2.326
1.599
2.440
0.001
1.302
0.570
7.165
69.718
0.496
7.894
130.771
4.405
0.525
848.804
14.141
7.807
6.391
50.234
39.629
0.421
0.010
99.119
0.000 •
60.125
0.000
0.000
0.000
o.oco
0.000
0.000
0.000
0.000
0.000
o.oco
1985 FULLY
ADJUSTED
NOX
815.154
1985 FULLY
ADJUSTED
NCX
0.018
0.026
4.052
5.525
1.624
1.996
0.370
9.302
17.591
12.201
0.033
10.107
2.406
38.259
0.258
0.073
2.732
7.817
0.243
0.037
29.687
46.456
22.219
1.358
0.965
14.512
1.203
0.300
1.265
0.000
1.394
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
1985 FULLY
ADJUSTED
VOC
1539.050
'935 FULL''
ADJUSTED
VCC
0.062
0.089
0.307
0.000
29.416
0.014
0.017
0.272
0.540
0.309
0.000
0.036
0.153
0.414
4.555
0.065
0.655
41.221
1.256
0.185
96.743
7.553
5.396
3.394
2.805
11.237
0.301
0.028
27.807
230.337
11.054
88.182
61.231
^2.j57
66.269
37.983
4.749
-61. -55
••0.165
19.730
2.C67
-------
EMISSIONS (TONS/OAr)
10.26 MONDAY,
1939
DESCRIPTION
Other Trans. Equip. Mfg.
Electrcal Equip. Mfg.
Ship Building and Repair
Misc. Ind. Mfg.
Misc. Ird. Solvent Use
POTWs
Cutback Asphalt Paving Oper.
Fugitives from SCCMI
Bulk Terminals and Sulk Plants
Process Ems. - Bakeries
Process 'Ems. - Pharm. Mfg.
Proc. Ems.- Synth. Fibers Mfg.
Crude Oil/Nat.Gas Prod. Fields
Hazardous Waste TSDFs
Alt CO
sec
90
91
92
93
95
100
101
102
103
105
106
107
108
109
OE=New roric
1985
UN ADJ.
CO
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
LAI tl>UKT=Nl
1985
UN ADJ.
NOX
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
JNMUblLt
1985
UNADJ.
voc
0.470
3.400
0.580
160.840
459.400
1.470
17.720
12.740
40.020
8.840
13.270
0.300
9.980
12.310
1985 FULLY
ADJUSTED
CO
0.000
0.000
0.000
0.000
0.000
c.ooo
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
1985 FULLY
ADJUSTED
NOX
0.000
0.000
0.000
O.OOC
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
',985 FULLY
ADJUST:-;
voc
0.470
3.400
0.580
160.840
-463.540
1.470
17.720
12.740
62.43C
8.840
13.270
0.300
9.980
14.770
1454.158
233.519
1694.770
1494.972
234.040
1936.810
-------
^MISSIONS
iO.36 MOMOAr , .iAY c.,
NcDS
DESCRIPTION
Solvent Metal Cleaning
Printing and Publishing
Fixed Roor Tanks - Crude Oil
Fixed rtr.cf '.-inks - Gasoline
EFR Tanks - Crude Oil
EFR T;nks - Sasol'ne
Bulk Gas Tirr..- 3ubm. .Balanced
Bulk Gas Ts:-"!.- Not Balanced
Acryloni en le Mfg.
SOCM! r-jg-t-vss
Petroleum Refinery Fugitives
Styrene- Butadiene Rubber Mfg.
Polyethylene Mfg.
Petr. Refinery UW Treatment
?tr. Refinery Vacuum Distil.
Paint and Varnish Mfg.
Rubber Ties .Ifg.
Automobile Surface Coating
Beverage Can Surface Coating
General Wooa Surface Coating
Paper Surface Coating
Misc. Surface Coating
Coke Oven Byproduct Plants
Ferrosilicon Prod.
Iron/Steel Blast Furn. .Sinter.
Marine Vessel Loading
Util. =.xt. Oomb. - Coal
Util. Ext. Cent). - Oil
Util. Ext. Comb. - Natural Gas
Util. Ext. Comb. - Other
Ind. cxt. Comb. - Other
Comm./tnst. Comb. - Coal
Comm./Inst. Comb. • Oil
Comm./Inst. Comb. - Gas
Comm./Inst. Comb. - Other
Waste Disposal
Ind. Int. Comb. - Gas Recip.
Util. Int. Comb. - Oil Turb.
Util. Int. Comb. - Gas Turb.
Cogeneration - Other
Ind.Ext.Ccno. - Ci 1, <1COMMSt'j/h
!r.d.E.xt.:omb. • Oi 1 .>1OOMM8t-Vh
.*C.J\C winO • -aa '• JC.^riB tu/ n
Ind. Ext. Comb.- Gas, <100MMBtu/h
SFAT::
PCD
1
2
4
5
6
7
7
10
18
'9
20
22
24
26
27
29
30
33
34
35
36
37
39
40
41
43
50
51
52
53
57
53
59
60
61
64
73
74
76
84
35
37
^
90
1985
uNADJ.
CO
497.277
0.000
0.000
0.000
0.000
0.000
O.OOC
c.cco
o.ono
0.037
0.000
0.000
0.000
0.000
0.000
174.796
0.000
0.000
0.000
0.000
0.000
0.000
0.000
2.397
0.000
59.533
0.000
43.143
0.121
0.016
0.002
0.008
3.288
0.033
0.266
0.003
19.641
3.842
0.046
0.008
12.692
0.017
0.333
~~ -
7.869
326.290
1985
U-JADJ.
NCX
53.970
0.000
0.300
0.000
n.oco
O.OOC
o.coc
O.COO
0.000
0.000
0.000
0.000
0.000
0.000
0.000
i.970
0.150
0.000
0.000
^ 0.000
0.000
0.000
0.000
0.560
0.000
0.400
0.000
1430.070
0.730
0.160
0.900
0.020
5.350
0.370
1.150
0.340
3.020
30.480
0.130
0.010
80.690
0 . i 00
5.010
' ~~- .~,
14.940
; 639. 230
j : ,-j i
1985
JNAOJ.
VOC
88.778
3.232
19.968
0.097
0.06".
0.219
0.709
0.4Z3
0.515
0.029
0.063
0.517
3.080
6.200
0.457
3.753
6.331
0.469
16.116
11.839
0.838
6.796
125.587
1.887
0.000
0.488
1.613
4.686
0.097
0.001
0.003
0.006
0.210
0.025
0.013
0.142
0.214
0.229
0.049
0.004
0.841
G.G23
0.457
- _~
0.780
3CC.062
1935 FULLY
^.D.uSTEO
CO
497.277
0.000
0.000
0.000
0.000
0.000
O.COO
0.000
0.000
0.037
0.000
0.000
0.000
0.000
0.000
174.796
. 0.000
c.oco •
0.000
0.000
0.000
0.000
0.000
2.397
0.000
59.533
0.000
43.143
0.121
0.016
0.002
0.008
3.288
0.033
0.266
0.003
19.641
3.842
0.046
0.008
12.692
O.Q17
0.333
' ~7 ~
7.869
225.290
1985 FULLY
AD JU-. • ;0
NOX
53.970
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
O.COO
0.000
0.000
0.000
0.000
0.000
4.970
0.150
0.000
0.000
0.000
O.COO
0.000
0.000
0.560
0.000
0.400
0.000
U30.070
0.730
0.160
0.900
0.020
5.350
0.370
1.150
0.340
3.020
30.480
0.130
0.010
80.690
3. ICC
5.010
14.940
1639.3SG
1935 FULLY
AO JUSTE:
VOC
88.778
3.232
19.968
0.097
0.061
0.219
0.709
0.433
0.515
0.029
0.063
0.517
3.080
6.200
0.457
3.758
6.381
.'.' . ;.69
16.116
11.839
0.3S3
6.796
125.587
1.887
0.000
0.488
1.613
4.636
0.097
0.001
0.003
0.006
0.210
0.025
0.013
0.142
0.214
0.229
0.049
0.004
0.841
•"- n~~z
0.^57
0.780
3CS.G62
-------
£HiSS!ONS (TONS/DAY)
iO.36 MONDAY, MAY 2, '.93? A--:
DESCRIPTION
..................... ........ — ___..,. NEDS
DESCRIPTION
Res. Fuel - Anth. Coal
Res. Fuel - Bit. Coal
Res. Fuel - Dist. Oil
Res. Fuel - Natural Gas
Res. Fuel - Wood
Comm/Inst. Fuel - Anth. Coal
Comm/Inst. Fuel - Bit. Coal
Comm/Inst. Fuel - Dist. Oil
CJimi/Inst. Fuel - Natural Gas
I no. Fuel - Bit. Coal
Ind. Fuel - Dist. Oil
ind. Fuel - Residual Oil
Ind. Fuel - Natural Gas
Incineration - Residential
Incineration - Industrial
Incineration - Comm/Inst.
Open Burning - Residential
Open Burning - Industrial
Open Burning - Camm/Inst.
Off -Highway Gas Vehicles
Off-Highway Diesel Vehicles
Railroad Locomotives
Aircraft - Military
Aircraft - Civil
Aircraft • Commercial
Vessels - Coal
Vessels - Diesel
Vessels - Gasoline
Gasoline Marketed
Forest Wildfires
Structural Fires
Degreasing
D'y Clean ing
"rgehie Arts/Printing
vjccer ina /•. Soti; .119.
Architectural Coating
Auto Body Repair
!1oto Venice ."if';.
Fabricated Metals
Machinery Mfg.
Furniture Mfg.
f: at s'ooa Products
sec
ALL
S-° A TC
i A 1 c
see
1
2
3
5
6
7
3
9
11
14
16
17
18
21
22
23
24
25
26
39
44
45
46
47
48.
49
50
52
54
60
64
78
79
fiO
„ *
82
83
.34
36
37
38
39
1985
JNAOJ.
:o
5486.010
CCO E =0h i Q
1985
UNADJ.
CO
0.014
'.023
0.136
0.764
77.114
0.036
0.425
0.509
2.365
4.883
1.860
0.309
11.075
227.305
0.851
6.311
131.163
7.497
0.701
705.610
28.056
20.805
6.109
54.360
15.271
14.550
0.049
46.418
0.000
3.224
35.726
0.000
0.000
0.000
J . -ww
0.000
0.000
G-00?
0.000
0.000
0.000
0.000
CATEGOR Y=MOB I LE
1935
UNAOJ.
>IOX
1985
JNAOJ.
voc
954.930 1033.800
CATEGORY=NONM08I LE • * —
1985 1985
UNADJ. UNADJ.
NCX
0.000
0.034
0.490
3.817
0.926
0.583
0.714
2.036
11.327
37.393
X 7.852
3.398
68.269
0.841
0.126
2.184
7.341
0.413
0.049
24.678
92.171
59.213
1.293
1.044
5.592
0.485
0.141
0.592
0.000
0.091
0.828
0.000
o.coc
o.occ
0.000
0.000
0.300
0.000
0.000
o.coo
o.con
voc
0.001
0.114
0.037
0.000
16.785
0.004
0.032
0.059
0.300
0.137
0.518
0.028
0.774
14.851
0.112
0.523
41.345
2.138
0.247
80.423
14.985
14.381
3.244
3.035
4.330
1.617
0.035
13.022
120.934
0.442
6.568
79.811
46.074
31.091
74.150
29.146
13.314
23.069
7.251
12.467
2.727
1985 FULLY
ADJUSTED
CO
5822.170
1985 FULLY
ADJUSTED
CO
0.014
1.028
0.136
0.764
77.114
0.036
0.425
0.509
2.365
4.383
1.860
0.309
1 1 .075
227.305
0.851
6.311
131.163
7.497
0.701
705.610
28.056
20.805
6.109
54.360
15.271
14.550
0.049
78.911
0.000
3.224
35.726
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
o.coo
o.occ
1985 FULLY
ADJUSTED
NOX
791.015
1985 FULLY
ADJUSTED
HCX
o.oco
0.034
0.490
3.817
0.926
0.583
T.7K
2.036
11 .227
37.893
7.852
3.398
68.269
0.841
0.126
2.184
7.841
0.413
0.049
24.678
92.171
59.213
1.298
1.044
5.592
0.485
0.141
1.007
0.000
0.091
0.828
0.000
O.COO
0.000
0.000
0.000
o.cco
0.000
0.000
0.000
o.cco
1985 FULLV
AC^JST:D
voc
1333.870
1985 FULLY
ADJUSTED
VOC
0.001
0.114
0.037
0.000
16.785
0.004
0.032
0.059
".'CO
0.137
0.518
C.02S
0.774
14.851
0.112
0.523
41.345
2.138
0.247
80.423
14.985
14.381
3.244
3.035
4.330
1.617
0.035
22.138
174.145
O.i42
6.568
79.811
46.C74
31 .091
126.054
29.146
13.314
23.069
7.251
12.467
2 . l~-~
-------
EMISSIONS (TCNS/DAr:
10.36 MCNDA1,', .'1AY 3, 1989 A--2
DESCRIPTION
Other Trans. Equip. Mfg.
ELectrcat Equip. Hfg.
Ship Building and Repair
Misc. Ind. Mfg.
Misc. '.nd. So I ven: Use-
?OTWs
Cutback Aschalt Psvinq Oper.
Fugitives -ran SOCMI
Su'.k r-3rminali and Sulk 3l.ancs
Petroleum Refinery Fugitives
Process ^ms. • Bakeries
Process Ems. • Pharm. Mfg.
Proc. Ems.- Synth. Fibers Mfg.
Crude Oil/Nat.Gas Prod. Fields
Hazardous Waste TSOFs
il Aic C
sec
90
91
92
93
•:?
100
'01
•02
:03
1C4
105
106
107
108
109
uut=umo
1985
UNADJ.
CO
0.000
0.000
0.000
0.000
0.000
o.oco
0.000
O.JOO
0.000
O.'JCO
0.000
0.000
0.000
0.000
0.000
LAI tbUKI=NO!
1985
u'rJADJ .
NOX
0.000
o.oco
o.oco
0.000
o.coc
0.000
0.000
3.000
0.000
0.000
o.coo
o.ccc
0.000
0.000
0.000
-------
•3MIS3;GNS (TCNS/GAV)
IC.jo MONDAY, HAY o, 1939
NEDS STATE CODE=Pennsylvam a CAIhGOKT=roiNI
DESCRIPTION
Solvent Metal Cleaning
Printing and Publishing
Fixed Roof Tanks - Crjde Oil
;;xed Roof Tanks Gdsaline
EFR Tanks - Cruae Oi I
3FR Tanks - Gasoline
3ulk Gas "orm.- iplasn Fill
3ulk -jds "arm.- Juan. .Balanced
Bulk Gas Term.- Not Balanced
SOCMI fugitives
Petroleum Refinery Fugitives
Styrene-Butadiene Rubber Mfg.
Polyethylene Mfg.
Petr. Refinery WU Treatment
Per. Sefinery Vacuum Oistil.
Paint and Varnish Mfg.
Automooi ie Surfacs boating
Beverage Can Surface Coating
General Wood Surface Coating
Paper Surface Coating
Misc. Surface Coating
Coke Oven Byproduct Plants
Iron/Steel Blast Furn. ,Sinter.
Pulp/Paper - Recovery Furnace
Marine Vessel Loading
Charcoal Mfg.
Util. =;iOOMMBtu/h
ina.cAi.'.omc. - Gas,> :UOMM8tu/n
Ind. Ext. Comb. -Cogeneration
Ind. Ext. Comb.- Gas,<100MMBtu/h
POD
1
2
4
-
6
7
2
•^
10
:9
20
22
24
26
i-r
29
33
34
35
36
37
39
41
42
43
46
50
51
52
53
57
58
59
60
63
64
72
73
74
76
34
•37
*Z
89
90
19S5
UNADJ.
CO
753.119
0.000
0.000
0.000
-.JCO
0.000
o.oco
0.000
o.coo
o.oco
0.019
0.000
0.000
0.000
0.000
16.256
O.OCO
J.OCO
0.000
0.000
0.000
0.000
8.132
111.188
8.634
0.000
0.450
33.296
3.412
0.042
0.057
0.000
3.721
0.014
0.106
0.452
34.853 •
O.S92
6.098
0.249
0.005
7.933
T.774
^.-•-'0
0.012
4.987
1985
UNADJ.
NOX
84.860
0.000
0.000
0.000
o.coo
0.000
C.JOO
0.000
u.OOO
0.000
0.000
0.000
0.000
0.000
0.000
4.630
0.000
c.oco
6.460
* 0.000
0.000
0.000
2.800
0.850
0.220
0.000
0.150
1384.380
40.140
0.580
2.010
0.650
4.430
0.160
0.510
2.050
4.070
2.240
48.240
1.150
0.020
54.310
8.890
3.
-------
EMISSIONS CTCI.S/OAV)
NEDS STATE CODE=Pennsylvania C
10.36 MONDAY, 1AY -3, 1989 A-i-
DESCRIPTION
DESCRIPTION
Res. Fuel - Anth. Coal
Res. Fuel - Sit. Coal
Res. Fuel - Dist. Oil
Res. Fuel - Natural Gas
Res. Fuel - Wood
Comm/Inst. Fuel - Anth. Coal
Comm/Inst. Fuel - Bit. Coal
Comm/Inst. Fuel - Dist. Oil
Comm/Insc. Fuel - Resic. Oil
Comm/Inst. Fuel - Natural Gas
Ind. Fuel - Dist. Oil
Ind. Fuel - Natural Gas
Incineration - Residential
Incineration - Industrial
Incineration - Comm/Inst.
Open Burning - Residential
Off-Highway Gas Vehicles
Off-Highway Diesel Vehicles
Railroad Locomotives
Aircraft - Military
Aircraft - Civil
Aircraft - Commercial
Vessels - Diesel
Vessels - Residual Oil
Vessels - Gasoline
Gasoline Marketed
Structural Fires
Degreasing
D rye lean ing
Graphic Arts/Printing
Rubber and Plastic Mfg.
Architectural Coating
Auto Body Repair
^0*0 ''ehicte "fg.
.-'cper Ji;afir,9
Fabricated Metals
Machinery Mfg.
Furniture Mfg.
". -C -ooa ~-~.2-^:-z
Other Trans. Equio. yfrj.
Electrcal Equip. Mfg.
Ship Building and Repair
Misc. Inc. Mfg.
sec
1985
UNADJ.
CO
ALL 4151.000
COOE=P6nnsy '. vsn 1 3
1985
UNADJ.
sec
1
2
3
5
6
7
8
9
10
11
16
18
21
22
23
24
39
44
45
46
47
48
50
51
52
54
64
78
79
30
81
82
33
84
,C
86
87
as
;9
90
91
92
93
CC
1.626
0.736
0.265
0.281
50.331
0.200
0.611
0.979
0.177
1.944
1.941
23.135
16.497
0.220
0.791
167.887
825.548
16.953
12.330
5.012
50.785
26.356
0.607
0.030
34.553
0.000
39.565
0.000
0.000
0.000
0.000
0.000
0.000
0.000
- . J C C
0.000
0.000
0.000
* . J C 3
0.000
0.000
0.000
o.cco
1935
UNADJ.
NOX
862.390
PATr'
V»M 1 C«
1585
UNACJ.
NOX
0.054
0.025
0.955
1.405
0.605
3.270
1.026
3.917
1.953
9.720
k 8.193
134.045
0.061
0.033
0.274
10.037
28.874
55.693
36.516
1.065
0.976
9.652
1.735
0.910
0.441
0.000
0.918
0.000
0.000
0.000
0.000
0.000
0.000
0.000
J . J3C-
0.000
0.000
0.000
"~3
0.000
0.000
0.000
G.OOC
Y=MOBILE --
1985
UNAQj .
VOC
876.420
:NONM08ILE *
1985
UNADJ.
VOC
0.181
0.082
0.072
0.000
10.955
0.023
0.047
0.114
0.060
0.246
0.540
1.491
1.078
0.029
0.066
52.921
94.093
9.055
3.368
2.662
2.836
7.473
0.434
0.084
9.694
113.329
7.274
59.302
38.828
38.963
69.787
81.758
30.479
4.301
16.264
6.472
11.7C3
0.445
1.790
0.159
122.370
1935 FULLY
ADJUSTED
CO
4869.730
1985 FULLY
ADJUSTED
CO
1.626
0.736
0.265
0.281
50.331
0.200
0.611
0.979
0.177
1.944
1.941
23.135
16.497
0.220
0.791
167.887
825.548
16.953
12.830
5.012
50.785
26.356
0.607
0.030
58.741
0.000
39.565
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0 QOC
0.000
0.000
0.000
0.000
1985 FULLY
ADJUSTED
NOX
717.090
1985 FULLY
ADJUSTED
NOX
0.054
0.025
0.955
1.405
0.605
3.270
1.026
3.917
1.953
9.720
8.193
134.045
0.061
0.033
0.274
10.037
28.874
55.693
36.516
1 .065
0.976
9.652
1.735
0.910
0.750
0.000
0.918
0.000
0.000
0.000
0.000
0.000
0.30C
0.000
0.000
0.000
3 . "CO
0.000
0.000
0.000
o.coo
1985 FULL':'
ADJUSTED
VOC
1189.750
1985 FULLY
ADJUSTED
VOC
0.181
0.082
0.072
0.000
10.955
0.023
0.047
0.114
0.06C
0.246
0.540
1.491
1.078
0.029
• 0.066
52.921
94.093
9.055
8.868
2.662
2.836
7.473
0.434
0.084
16.479
163.194
7.274
59.302
38.328
38.963
69.787
138.988
30. -79
4.801
16.264
6.472
' 1 . 70S
0.445
1.790
0.159
I22.o70
-------
£HI33iCNS (TCNS/OAYj
36 MONDAY, MAY
NEDS STATE
DESCRIPTION
Misc. Ind. Solvent Use
POTWs
Cutback Asphalt Paving Oper.
Fugitives from SOCHI
Bulk "?rminals and Sulk Plants
Petroleun Refinery Fugitives
Process Ems. - Bakeries
Process =ms. - Pharm. Mfg.
Proc. Eras.- Synth. Fibers Mfg.
Crude Oil/Nat.Gas Prod. Fields
Hazardous Waste TSOFs
tUUt:
sec
95
100
101
102
"03
•04
105
-.06
107
108
109
=rennsylvani ;
1985
UNAOJ.
CO
0.000
0.000
0.000
0.000
c.coo
o.oco
o.oco
o.oco
0.000
0.000
0.000
J LAItljUK
1985
UNADJ.
NOX
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
o.coo
0.000
0.000
T=NUNMUHlLt •
1985
UNADJ.
VOC
317.570
1.360
18.720
13.060
52.500
104.540
10.600
10.770
5.180
8.260
60.820
1985 FULLY
AO. LISTED
CO
0.000
o.oco
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
1985 FULLY
ADJUSTSO
NOX
0.000
0.000
0.000
0.000
0.000
o.oco
0.000
0.000
0.000
0.000
0.000
1985 FULLY
ADJUSTED
VOC
320.440
1.360
18.720
18.060
77.710
104.540
10.600
10.770
5.180
8.260
72.980
1279.863
312.350
1473.530
1304.050
312.660
1627.630
-------
EMISSIONS
iO.36 MGNOAV, AA!
DESCRIPTION
Solvent Metal Cleaning
Printing and Publishing
Dry Cleaning
EFR Tanks - Gasoline
Bulk Gas Term.- Splash rill
Service Stations - Stage I
Automobile Surface Coating
Beverage Can Surface Coating
Paper Surface Coating
Misc. Surface Coating
Util. Ext. Comb. - Oil
Util. Ext. Comb. - Natural Gas
Comm./Inst. Comb. - Oil
Comm./Inst. Comb. - Gas
Ind.Ext.Comb.- Cogeneraticn
Ind.Ext.Comb.- Oil,>100MMBtu/h
ilt LU
POO
1
2
3
7
a
M
33
34
36
37
51
52
59
60
36
87
ut=xnoae isiai
1985
UNADJ.
CO
0.019
0.000
0.000
O.COC
o.oco
0.000
0.000
0.000
0.000
0.000
0.000
0.099
0.467
0.025
0.016
0.020
0.015
0.669
-ia LA i tu
1935
DNA2J.
NOX
0.832
0.000
0.009
O.OCO
O.COO
0.000
o.oco
o.:oc
0-003
O.JOO
0.000
1.319
6.372
0.358
0.267
Z.Z',2
C.160
9.636
1985
'JfiAJJ.
VOC
2.942
0.036
3.665
0.005
0.032
0.156
0.014
o.rso
2.084
3.381
4. 789
0.023
0.008
0.010
0.000
0.008
0.007
18.468
1935 FULLY
ADJu3TcD
CO
0.019
0.000
0.000
0.000
0.000
0.000
0.000
0.000
o.coo
0.000
o.coo
0.099
0.467
0.025
0.016
O.C30
0.0.15
0.669
1935 FULLY
ACJU57ED
NOX
0.832
0.000
0.009
0.000
0 . JCO
0.000
o.coc
o.coo
0.003
0.000
o.coc
1.319
6.372
0.358
0.267
0.312
0.160
9.636
1935 FULLY
ADJUSTED
VOC
2.942
0.036
3.665
0.005
0.082
0.156
0.014 •
0.7;0
2.084
3.381
4.739
C.023
0.008
0.010
0.000
C.CC3
.0.007
13.463
-------
'. fONS/DAY)
NEDS STATE COOE=Rhode Island
1C.36 MONDAY, MA',' 3, ;
1985
uriACJ.
DESCRIPTION SCC CO
ALL 218.580
1985
OESCRIPTIOM
Res. Fuel - Anth. Coal-
Res. Fue1- - Dist. Oi'.
Res. Fuel - Natural Gas
Res. Fuel - Wood
Comm/Inst. Fuel - Anth. Coal
Comm/Inst. Fuel - Dist. Oil
Comm/Inst. Fuel - Natural Gas
Ind. Fuel • Sit. Coal
I.Td. .-"-je1. - Gis:. Q~.\
Ind. Fuel - Residual Oil
Ind. Fuel - Natural Gas
Incineration - Residential
Incineration - Industrial
Incineration - Comm/Inst.
Open Burning - Residential
Open Burning - Industrial
Open Burning - Comm/Inst.
Off -Highway Gas Vehicles
Off -Highway Oiesal Vehicles
Railroad Locomotives
Aircraft - Military
Aircraft - Civil
Aircraft - Commercial
Vessels - Diesel
Vessels - Gasoline
Gasoline Marketed
Structural Fires
Degreasing
0 rye I can ing
Graphic Arts/Printing
Rubber and Plastic Mfg.
Architectural Coating
Auto 3ody Sepair
Moto Vehicle Mfg.
.-jper .waf.r.g
Fabricated Metals
Machinery Mfg.
Furniture 'Ifg.
Other Trgpg. cauio. Mfq.
Electrcai Equip. Mfg.
Ship Building and Repair
Misc. Ind. Mfg.
3CC
1
3
5
6
7
9
: •
14
16
17
18
21
22
23
24
25
26
39
44
45
46
47
48
50
52
54
64
78
79
50
81
82
33
84
,2
86
87
23
=0
91
92
93
UN ADJ.
:o
0.007
0.040
0.018
1.968
0.002
0.080
o.;i9
0.031
o.-.oo
0.206
0.394
17.253
0.015
0.069
6.015
0.342
0.058
68.384
0.676
0.097
0.190
5.638
1.384
0.093
4.515
0.000
3.177
0.000
0.000
0.000
0.000
0.000
0.000
0.000
•' ".
0.000
0.000
0 . CCO
0.000
0.000
0.000
0.000
CAItGC
1935
UNAud .
NOX
}KT=MOBll.t --
1985
UN ADJ.
voc
66.770 67.140
CATEGQRY=NONM08 I LE •
1985 1985
UN ADJ. UN ADJ.
NOX
0.000
O.i4i
0.089
0.023
0.029
0.320
0.592
0.243
0.42:
2.263
1.879
0.063
0.002
0.023
0.359
0.018
0.004
2.391
2.220
0.275
0.040
0.108
0.506
0.264
0.057
0.000
0.073
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
j.COO
0.000
0.000
0.000
0.000
voc
0.001
0.011
0.000
0.428
0.000
0.009
0.015
0.001
O.C28
0.019
0.019
1.127
0.002
0.006
1.896
0.098
0.021
7.794
0.361
0.067
0.101
0.315
0.392
0.066
1.267
9.732
0.584
11.202
3.377
3.064
10.313
6.672
2.390
0.292
3.460
0.608
1.221
0.004
0.220
0.396
iH.256
1985 FULLY
ADJUSTED
CO
377.178
1985 FULLY
ADJUSTED
CO
0.007
0.040
0.018
1.968
0.002
0.080
0.119
0.031
0.100
0.206
0.394
17.253
0.015
0.069
6.015
0.342
0.058
68.384
0.676
0.097
0.190
5.638
1.384
0.093
9.030
0.000
3.177
0.000
0.000
0.000
0.000
0.000
o.:ao
0.000
0.000
0.000
c.ooo
0.000
J.OOO
0.000
0.000
1935 FULLY
ADJUSTED
NOX
53.240
1985 FULLY
ADJUSTED
NOX
0.000
0.144
0.089
0.023
0.029
0.320
0.592
. .0-243
0.-33
2.263
1.879
0.063
0.002
0.023
0.359
0.018
0.004
2.391
2.220
0.275
0.040
0.108
0.506
0.264
0.115
0.000
0.073
O.GOO
0.000
0.000
0.000
0.000
c.ooo
0.000
-1
0.000
0.000
T.OCO
0.000
0.000
0.000
o.oco
1985 FULLY
ADJUSTS;
voc
102.770
"985 FULLY
ADJUSTED
VOC
0.001
0.011
0.000
0.428
0.000
0.009
0.015
0.001
:.02£
0.019
0.019
1.127
0.002
0.006
1.396
0.098
0.021
7.794
0.361
0.067
0.101
0.315
0.392
0.066
2.533
14.988
0.584
11.202
3.377
2.064
10.313
13.345
2.390
0.292
3.460
0.608
1 .221
0.004
0.220
0.396
1 4.256
-------
NEDS STATE COOE=F
DESCRIPTION SCC
Misc. Ind. Solvent Use 95
POTUs 100
Cutback Asphalt Paving Oper. 101
Fugitives from SOCMI 102
Sulk Terminals 2nd 3u!k Plants 103
Process Ems. - Bakeries !05
Proc. E.rs.- Synth. Fibers Mfg. 107
IISSICNS CTC
hode islarx
1985
UN ADJ.
CO
0.000
0.000
0.000
0.000
0.000
0.000
0.000
110.870
:NS/CAY;
J CATEGORY
1985
UN ADJ.
NOX
0.000
0.000
0.000
0.000
0.000
0.000
0.000
12.422
'.C.36 MC.'iCAV, MAY
589
UNHUblLt '
1985
UNAOj.
VOC
28.975
0.267
0.769
1.782
3.630
0.332
0.605
122.510
1985 FULLY
ADJUSTED
CO
0.000
0.000
0.000
0.000
0.000
0.000
0.000
115.385
1985 FULLY
AOJU:TE:
NOX
0.000
0.000
0.000
0.000
0.000
0.000
0.000
12.479
1985 FULLY
ADJUSTED
VOC
29.236
0.257
0.769
1.782
5.735
C.332
0.605
133.071
-------
cMiSGIONS (TONS/CAY)
MONDAY, HAY 3, ',939 A-31
NED:
DESCRIPTION
Solvent Metal Cleaning
Printing and Publishing
Rubber Tire Mfg.
Automobile Surface Coating
General Wood Surface Coating
Paper Surface Coating
Util. Exc. Comb. - Coal
Util. Ext. Comb. - Oil
Util. Ext. Comb. - Natural Gas
Util. Ext. Comb. - Other
Comm./Inst. Comb. - Oil
Comm./Inst. Comb. - Gas
Util. Int. Comb. - Oil Turb.
Cogeneration - Other
Ind. Ext. Comb.- Oi l,>100MMBtu/h
Ind. Ext. Comb. -Cogeneration
Ind. Ex:. Comb.- GaS,
-------
EMISSIONS uGNS/OAf)
10.36 MONDAY, MAY 5, 1989 A-33
DESCRIPTION
UCrtC
DESCRIPTION
Res. Fuel - Anth. Coal
Res. Fuel • Dist. Oil
Res. Fuel - Natural Gas
Res. Fuel - Wood
Comm/Inst. Fuel - Anth. Coal
Comm/Inst. Fuel - Bit. Coal
Comm/Inst. Fuel - Dist. Oil
Comm/Inst. Fuel - Natural Gas
Ind. Fuel - Anth. Coal
Ind. Fuel - Bit. Coal
Ind. Fuel - Coke
Ind. Fuel - Dist. Oil
Ind. Fuel - Natural Gas
Incineration - Residential
Incineration - Industrial
Incineration - Comm/Inst.
Open Burning - Residential
Off-Highway Gas Vehicles
Off-Highway Diesel Vehicles
Railroad Locomotives
Aircraft - Military
Aircraft - Civil
Aircraft - Commercial
Vessels - Diesel
Vessels - Gasoline
Gasoline Marketed
Forest Wildfires
Agricultural Field Burning
Structural Fires
Degreasing
D rye lean ing
Graphic Arts/Printing
Rubber and Plastic Mfg.
Architectural Coating
,-oiro joay Repair
Moto Vehicle Mfg.
Paper Coating
'•aoricaced Metals
'3crir,~ry ''- = .
Furniture Mfg.
Flat Wood Products
Other Trans. Equip. Mfg.
Electrcal Equip. Mfg.
1985
UN ADJ.
SCC CO
ALL 255.330
STATE COO E= Vermont
SCC
1
3
5
6
7
8
9
11
•3
14
15
16
18
21
22
23
24
39
44
45
46
47
48
50
52
54
60
62
64
73
79
80
31
32
OJ
84
85
36
T~*
88
89
90
91
1985
UNADJ.
CO
0.018
0.057
0.009
9.661
0.005
0.209
0.103
0.027
0.004
0.041
0.024
0.125
0.057
8.004
0.023
0.218
15.056
61.871
2.112
0.259
0.355
5.328
1.407
0.022
4.902
0.000
0.085
0.000
1.484
0.000
0.000
0.000
0.000
o.oco
0. ^CC
0.000
0.000
0.000
J . _ J \J
0.000
0.000
0.000
0.000
U«l ELlUKI=ni
1985
•JNAOJ.
MOX
JBILt
1985
UNADJ.
voc
53.360 53.520
1985 1985
UNADJ. UNADJ.
NOX
0.001
0.204
0.046
0.116
0.081
0.351
0.412
0.133
O.C80
0.319
0.047
0.529
0.239
0.029
0.003
0.075
0.900
2.163
6.937
0.736
0.075
0.102
0.515
0.061
0.062
0.000
0.002
0.000
0.034
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
,* •"•I •"•,
0.000
0.000
0.000
0.000
voc
0.002
0.015
0.000
2.102
0.000
0.016
0.012
0.003
0.000
0.001
0.000
0.034
0.002
0.522
0.003
0.018
4.745
7.051
1.128
0.178
0.188
0.297
0.398
0.015
1.375
6.396
0.011
0.000
0.272
3.808
1.387
2.055
3.550
3.679
0.074
3.023
0.951
0.318
0.165
0.033
0.194
1985 FULLY
ACJUCT^D
CO
270.851
1985 FULLY
ADJUSTED
CO
0.018
0.057
0.009
9.661
0.005
0.209
0.103
. 0.027
0.004
0.041
0.024
0.125
0.057
8.004
0.023
0.218
15.056
61.871
2.112
0.259
0.355
5.328
1.407
0.022
9.803
0.000
0.085
0.000
1.484
O.COO
0.000
0.000
0.000
0.000
0.000
0.000
O.COO
o.ono
o.eoo
O.COO
o.ooc
1985 FULLY
ADJUSTED
NOX
43.252
1985 CULLY
ADJUSTED
MOX
0.001
0.204
0.046
0.116
0.081
0.351
0.412
0.133
0.080
0.319
0.047
0.529
0.239
0.029
0.003
0.075
0.900
2.163
6.937
0.736
0.075
0.102
0.515
0.061
0.125
0.000
0.002
0.000
0.034
O.COC
0.000
0.000
0.000
o.ooc
0.000
0.000
0.000
0.000
0.000
0.000
O.GOC
1985 FULLY
ADJUSTED
VOC
69.047
1985 FULLY
ADJUSTED
VCC
0.002
0.015
0.000
2.102
0.000
0.016
0.012
0.003
0.000
0.001
0.000
0.034
0.002
' 0.522
0.003
0.018
4.745
7.051
1.128
0.178
0.188
0.297
0.393
0.015
2.750
10.566
0.011
0.000
0.272
3.8C8
1.387
2.055
3.. =30
8.831
0.074
3.023
9.951
0.318
0.165
O.C33
J . 1 94
-------
EMISSIONS (TONS/DAY) ',0.56 MONDAY, MAY 3, 1989
DESCRIPTION
Ship Building and Repair
Misc. ind. Mfg.
Misc. Ind. Solvent Use
POTWs
Cutback Asphalt Paving Oper.
Bulk Terminals and Sulk Plants
Process Ems. - Bakeries
Process Ems. - Pharni. Mfg.
Hazardous Waste TSDFs
ATE Ct
sec
92
93
95
100
101
103
105
106
109
)DE=vermont
1985
UNADJ .
CO
0.000
0.000
0.000
0.000
0.000
O.OGO
0.000
0.000
0.000
UAI tliUKT=*
1985
UNADJ.
NOX
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
4UNMUblLt
1985
UNrtDu .
voc
0.007
5.352
14.171
0.028
0.566
2.719
0.186
0.011
0.030
1985 FULLY
ADJUSTED
CO
0.000
0.000
0.000
0.000
0..000
0.000
0.000
0 . 000
0.000
1985 FULLY
ADJUSTED
NOX
0.000
0.000
0.000
0.000
0.000
0.000
0.000
o.ooc
0.000
1985 FULLY
ADJUSTED
VOC
0.007
5.352
14.299
0.028
0.566
4.601
0.186
0.011
0.036
111.465 14.263 69.773 116.366 14.326 82.486
-------
EMISSIONS ;:;.N5,'DAr;
1C.36 MCNCAr, MAY ^l 198? A-55
Ntus siAit Luut=virgima L«ICIJUKI=KUINI
DESCRIPTION
Solvent Metal Cleaning
Printing and Publishing
Dry Cleaning
Fixed Rcof Tanks - C.-jde Oil
Fixed Roof Tanks - Gasoline
EFR Tanks - Crude Oil
EFR Tan<3 • Gasoline
Bulk Gas Term.- Subm. .Balanced
Bulk Gas Term.- Not Balanced
Service Stations - Stage I
Cellulose Acetate Mfg.
Polyethylene Mfg.
Ptr. Refinery Vacuum Distil.
Vegetable Oil Proc.
Paint and Varnish Mfg.
Rubber Tire Mfg.
Green "ire Spray
Automobile Surface Coating
Beverage Can Surface Coating
General Wood Surface Coating
Misc. Surface Coating
Coke Oven Byproduct Plants
Pulp/Paper - Recovery Furnace
Marine Vessel Loading
Single Chamber Incinerators
Charcoal Mfg.
Util. Ext. Comb. - Coal
Util. Ext. Comb. -Oil
Util. Ext. Comb. - Natural Gas
Ind. Ext. Comb. - Other
Comm./Inst. Comb. - Coal
Comm./Inst. Comb. - Oil
Comm./Inst. Comb. - Gas
Comm./Inst. Comb. - Other
Waste Disposal
Ind. Int. Comb. - Oil Recip.
Util. Int. Comb. - Oil Turb.
Util. Int. Comb. - Gas Tcrb.
Cogeneration - Other
Ind. Ext. Comb.- Oi I ,>100MMBtu/h
Ind.Hxt.Comb. - Gas, >100MM8~'j/h
Ind. Ext. Comb.- Gas, <100HM3tu/h
POD
1
2
3
4
5
6
7
9
10
11
21
24
27
28
29
30
31
33
34
35
37
39
42
43
44
46
50
51
52
57
58
59
60
61
64
71
74
76
84
87
38
90
1985
UNADJ.
CO
61.156
0.000
0.000
0.000
0.000
o.coo
0.000
o.ooc
0.000
0.000
0.000
o.coo
0.000
2.537
0.000
0.000
0.004
o.oco
0.000
0.000
0.000
0.000
0.728
30.030
0.000
1.901
5.247
6.490
0.445
0.140
0.000
0.544
0.283
0.011
0.400
0.411
0.000
0.023
0.027
6.070
0.804
0.258
10.907
1985
UNADJ.
NOX
49.836
0.000
0.000
0.000
O.QOO
0.000
0.000
0.000
0.000
0.000
0.000
o.oco
0.000
0.874
0.000
0.000
0.000
0.000
0.000
A* 0.000
0.000
0.000
0.038
2.733
0.000
0.192
0.000
230.151
3.498
1.056
0.075
1.214
2.191
0.059
. 0.042
0.717
0.000
0.102
0.096
79.697
8.108
3.512
9.163
1985
UNADJ.
VOC
135.265
3.110
34.308
0.183
0.790
0.0:3
0.108
4.935
2.033
3.346
0.054
5.832
0.190
2.265
2.284
1.305
8.086
1.432
33.565
10.786
12.917
0.602
0.264
0.077
1.206
0.279
4.788
0.671
0.093
0.003
0.003
0.011
0.047
0.000
0.007
0.074
0.000
0.000
0.000
0.314
0.032
0.002
2.269
1985 FULLY
ADJUSTED
CO
61.156
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
2.537
0.000
0.000
0.004
0.200
0.000
0.000
0.000
0.000
0.728
30.030
0.000
1.901
5.247
6.490
0.445
0.140
0.000
0.544
0.283
0.011
0.400
0.411
0.000
0.023
0.027
6.070
0.804
0.253
10.907
1985 FULLY
ADJUSTED
NOX
49.836
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.874
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.038
2.733
0.000
0.192
0.000
230.151
3.498
1.056
0.075
1.214
2.191
0.059
0.042
0.717
0.000
0.102
0.096
79.697
8.108
3.512
9.168
1935 FULLY
ADJUSTS}
VOC
135.265
3.110
34.308
0.183
0.750
0.058
0.108
4.935
2.033
3.346
0.054
5.332
0.190
2.265
2.284
1.305
8.086
1.432
33.565
10.786
12.917
0.602
0.264
0.077
1.206
0.279
4.788
0.671
0.093
0.003
0.003
0.011
0.047
0.000
0.007
0.074
0.000
0.000
0.000
0.314
0.032
O.OC2
2.269
128.416
393.359
273.594
128.416
393.359
273.594
-------
NEDS STATE
DESCRIPTION
. NEDS
DESCRIPTION
Res. Fuel - Anth. Coal
Res. "uel - Bit. Coal
Res. Fuel - Dist. Oil
Res. Fuel - Natural Gas
Res. Fuel - Uood
Comm/Inst. Fuel - Anth. Coal
Comm/Inst. Fuel • 3it. Coal
Comm/Inst. Fuel - Dist. Oil
Comm/Inst. "jet - Resid. Oil
Comm/Inst. Fuel - Natural Gas
Ind. Fuel - Bit. Coal
Ind. Fuel - Dist. Oil
Ind. Fuel - Natural Gas
Incineration - Residential
Incineration - Industrial
Incineration - Comm/Inst.
Open Burning - Residential
Open Burning - Industrial
Off -Highway Gas Vehicles
Off-Highway Diesel Vehicles
Railroad Locomotives
Aircraft - Military
Aircraft - Civil
Aircraft - Commercial
Vessels - Diesel
Vessels - Residual Oil
Vessels - Gasoline
Gasoline Marketed
Forest Wi Idf ires
Managed Burning - Prescribed
Structural Fires
D eg r easing
0 rye lean ing
Graohic Arts/Printing
Architectural Coating
Auto Body Repair
Hcto Vehicls Mfg.
'-"•a1* '23-'--
Fabricated Metals
Machinery rtfg.
Furniture Mfg.
Flat Wood Products
sec
iMISSiCNS (TCN3/DAY)
CODE=Virginia CATEGORY=M08ILE
1985 1985 1985
UNADJ.
CO
ALL 2626.570
STATE CCDE=Vi rg i ni a
1985
UNADJ.
5CC
1
2
3
5
6
7
8
9
10
11
14
16
18
21
22
23
24
25
39
44
45
46
47
48
50
51
52
54
60
61
(A
78
79
80
82
83
34
"e
86
37
88
39
CO
0.044
0.799
0.157
0.125
66.372
0.002
0.329
0.353
0.087
0.565
2.815
0.474
4.175
6.736
0.379
1.029
84.316
0.766
322.758
15.501
23.414
7.022
32.617
10.285
2.141
0.040
31.131
0.000
2.880
0.000
13.693
0.000
O.OCO
0.000
• "-• n.
0.000
0.000
0.000
-, ,„-,
0.000
0.000
0.000
o.coo
UNADJ.
NOX
UHADJ.
voc
536.740 559.450
pATCpnQv— LiniJMnn T i c .-.
LA 1 tuUK I — NUNMUo I LC
1985 1985
UNADJ. UNADJ.
NOX
0.001
0.026
0.565
0.624
0.797
0.037
0.552
1.412
0.953
2.824
1 21.848
2.000
25.051
0.024
0.056
0.355
5.040
0.042
11.288
50.925
66.640
1.492
0.626
3.766
6.116
1.201
0.397
0.000
0.081
0.000
0.317
0.000
o.ooc
0.000
0.000
0.000
0.000
- -~~
0.000
0.000
0.000
o.oco
voc
0.005
0.089
0.043
0.000
14.446
0.000
0.025
0.041
0.029
0.072
0.079
0.131
0.282
0.440
0.050
0.085
26.578
0.218
36.787
8.280
16.185
3.729
1.821
2.916
1.529
0.110
8.734
69.820
0.395
0.000
2.517
19.015
28.253
12.539
39.658
17.241
1.351
"> n -"^
2.653
1.941
10.055
1.329
;o.-:o M'
1985 FULLY
ADJUSTED
CO
3057.890
1985 FULLY
ADJUSTED
CO
0.044
0.799
0.157
0.125
66.372
0.002
0.329
0.353
0.087
0.565
2.815
0.474
4.175
6.736
0.379
1.029
84.316
0.766
322.758
15.501
23.414
7.022
32.617
10.285
2.141
0.040
40.471
0.000
2.880
0.000
13.693
0.000
0.000
0.000
0.000
0.000
0.000
" ""0
o.oco
0.000
o.oco
G.OCC
UNUAT, MAT 3,
1985 FULLY
ADJUSTED
NOX
452.536
1985 FULL/
ADJUSTED
NCX
0.001
0.026
0.565
0.624
0.797
0.037
0.552
1.412
0.953
2.824
21.848
2.000
25.051
0.024
0.056
0.355
5.040
0.042
11.288
50.925
66.640
1.492
0.626
3.766
6.116
1.201
0.516
0.000
0.081
0.000
0.317
0.000
:.:oo
0.000
0.000
0.000
0.000
1 -~-l
0.000
0.000
o.oco
0 . COG
1 rOY n-.O
1985 FULLY
ADJUSTED
VOC
759.680
1985 FULLY
ADJUSTED
VOC
0.005
0.089
0.043
0.000
14.446
0.000
0.025
0.041
0.029
0.072
0.079
0.131
0.282
0.440
0.050
0.085
26.578
0.218
36.787
8.280
16.185
3.729
1.821
2.916
1.529
0.110
11.354
96.351
0.395
0.000
2.517
19.015
23.253
12.539
67.419
17.241
1.351
-n - ' «
2.538
1.941
10.055
1 .329
-------
EMISSIONS
TC.'JS/OA'r
iu.36 MONDAY, HAY
!939
DESCRIPTION
Other Trans. Equip. Mfg.
Electrcal Equip. Mfg.
Ship Building and Repair
Misc. !nd. Mfg.
Misc. 'rd. Solvent Use
POTWs
Cutback Asphalt Paving Oper.
Fugitives from SCOi!
Bulk Terminals 3rd Sulk Plants
Petroleum Refinery Fugitives
Process Ems. - Saksr-js
Process Ems. - Pharm. Mfg.
Proc. Ems.- Synth. Fibers Mfg.
Crude Oil/Nat.Gas Prod. Fields
Hazardous Waste TSDFs
1 1 C LUl
sec
90
91
92
93
="5
100
-101
"02
:03
104
'05
106
107
108
109
Jt=vi rgini a
1985
UNACU.
CO
0.000
O.OOC
0.000
0.000
0.000
0.000
0.000
O.GOC
0.300
0.000
0.000
0.000
0.000
0.000
0.000
LAI CUUKT=!
1935
UrtMCJ.
MOX
0.000
0.000
0.000
0.000
T.CCO
O.JOO
0.000
o.;co
0.000
o.ooc
0.000
0.000
0.000
0.000
0.000
^UHnUB 1 LC - - -
1985
L«AOo .
voc
0.022
0.733
5.016
43.795
'42.563
0.483
14.739
12.274
29.529
7.846
3.069
1.692
55.828
0.813
6.228
1985 FULLY
ADJUSTED
CO
0.000
0.000
0.000
0.000
o.oco
o.coo
0.000
O.JCO
0. JOO
0.000
0.000
0.000
0.000
0.000
0.000
1935 FULLY
AD-uSTcD
NOX
0.000
0.000
0.000
0.000
o.coo
o.ooq
0.300
o.:oo
0 000
0.000
0.000
0.000
0.000
0.000
0.000
1935 FULLY
A3JU3TID
voc
0.020
0.730
5.020
43.300
143.950
0.433
',4.739
'2.27;
^2.286
7.846
3.069
1.692
55.828
0.813
7.473
631.002
205.072
695.030
640.342
205.190
757.230
-------
;0.36 MONDAY, MAY 3, I>39
DESCRIPTION
Fixed Roof Tanks - Crude Oil
Fixed Roof Tanks - Gasoline
EFR Tanks - Crude Oil
^FR Tanks - Gasol'-?
Sulk Gas 7ertn.- Not Balanced
SOCHI Fugitives
Petrole-an Refinery Fugitives
Polyecnylane Mfg.
Petr. Refinery WW Treatment
Paint snd ''arnish Mfg.
Caroon Slack Mfg.
Automobile Surface Coating
Beverage Can Surface Coating
General Wood Surface Coating
Misc. Surface Ccat'lng
Coke Oven Byproduct Plants
Ferros;'. icon "'rsd.
Iron/Steel Blast Furn.,Sinter.
Util. Ext. Comb. - Coal
Util. Exc. Comb. - Oil
Util. Ext. Comb. - Other
Ind. Ext. Comb. - Other
Comm./Inst. Comb. - Coal
Comm./Inst. Comb. - Gas
Comm./Inst. Comb. - Other
Waste Disposal
Ind. Int. Comb. - Gas Turb.
Ind. Int. Comb. - Gas Recip.
Cogeneration - Other
Ind.Ext.Comb.- Oil,>100MMBtu/h
Ind.Ext.Comb.- Gas,>100MMBtu/h
Ind.Ext.Comb.- Gas,<100MMBtu/h
,TE CODE=Uest Virginia CAr£GORY=POiN r
POO
4
5
6
7
10
19
20
24
26
29
32
33
34
35
37
39
40
41
50
51
53
57
58
60
61
64
n
73
84
87
88
90
1935
UNADJ .
CO
123.915
0.000
O.OOC
0.000
T.GQO
0.000
0.000
C.GCO
O.OC3
0.000
0.000
147.929
0.000
0.000
0.000
o.coc
1.124
0.000
123.422
27.894
0.079
0.260
0.000
0.212
0.069
0.000
0.022
0.590
5.324
3.727
0.274
1.075
0.741
1985
UNADJ.
NOX
63.270
0.000
0.000
0.000
O.OOC
0.000
0.000
0.000
0.240
0.000
0.000
0.040
0.000
0.010
0.000
0.000
0.120
0.010
0.970
* 943. 170
0.370
0.180
0.190
0.240
0.130
0.000
0.010
1.340
37.700
51.690
3.000
7.380
1.820
1985
UNADu .
VOC
102.815
1.064
0.526
0.012
0.149
0.211
5.591
O.J52
5.996
1.418
0.005
2.373
2.067
3.088
2.966
1.817
3.474
3.872
7.464
3.250
0.006
0.056
0.001
0.003
0.009
0.001
0.001
0.015
0.240
0.194
0.016
0.016
0.002
1985 FULLY
ADJUSTED
CO
123.915
0.000
o.coo
0.000
0.000
0.000
0.000
c.ooo
0.003
o.cco
0.000
147.929
0.000
0.000
0.000
0.000
1.124
0.000
128.422
27.894
0.079
0.260
0.000
0.212
0.069
0.000
0.022
0.599
5.324
3.727
0.274
1.075
0.741
1985 FULLY
ADJUSTED
NOX
63.270
0.000
o.coo
0.000
o.son
o.oco
0.000
o.cco
0.240
O.COO
0.000
0.040
0.000
0.010
0.000
o.oco
0.120
0.01C
0.970
943.170
0.370
0.180
0.190
0.240
0.130
0.000
0.010
1.340
37.700
51.690
3.000
7.380
1.820
1985 FULLV
ADJUSTS:
VOC
102.815
1.064
0.526
0.012
0.%9
0.211
5.691
3. 552
5.996
1.418
O.C05
2.373
2.067
3.088
2.966
1.317
3.474
3.872
7.464
3.250
0.006
0.056
0.001
0.003
0.009
0.001
0.001
0.015
0.240
0.194
0.016
0.016
0.002
441.668
1111.850
149.469
441.668
1111.850
149.469
-------
EMISSIONS .'TONS/DAY)
10.36 MONDAY, .MAY 3, 1989 A-59
NEDS STATE coofc=uest Virginia LAI tuuKT=MufcHLt
DESCRIPTION
••••-•• UCnCCTATC
DESCRIPTION
Res. Fuel - Bit. Coal
Res. Fuel - Cist. Oil
Res. Fuel - Natural Gas
Res. Fuel - Wood
Comm/Inst. Fuel - Anth. Coal
Comm/Inst. Fuel - Dist. Oil
Comm/Inst. Fuel - Resia. Oil
Comm/Inst. Fuel - Natural Gas
Ind. Fuel - 3it. Coal
Ind. Fuel - Dist. Oil
Ind. Fuel - Natural Gas
Incineration - Residential
Open Burning - Residential
Open Burning - Industrial
Off -Highway Gas Vehicles
Off-Highway Diesel Vehicles
Railroad Locomotives
Aircraft - Military
Aircraft - Civil
Aircraft - Commercial
Vessels - Diesel
Vessels - Gasoline
Gasoline Marketed
Forest Wi Idf ires
Structural Fires
D eg r easing
D rye lean ing
Graphic Arts/Printing
Rubber and Plastic Mfg.
Architectural Coating
Auto Body Repair
Moto Vehicle Mfg.
Paper Coating
Fabricated Metals
iiacninery nig.
Furniture Mfg.
Flat Wood Products
Other Trans. £qu;p. ,113.
Shio <3uitd:r.q and Secair
Misc. Ind. Mfg.
Misc. Ind. Solvent Use
POTWs
sec
1985
UNADJ.
CO
ALL 697.680
COOE=Wss t Vi rg i n 1 3
1585
UN ADJ. '
3CC
2
3
5
6
7
9
10
11
14
16
18
21
24
25
39
44
45
46
47
48
50
52
54
60
64
78
79
80
81
82
83
84
85
36
d/
88
89
90
/ "!
92
93
95
100
CO
0.227
0.015
0.083
27.694
0.006
0.119
0.001
0.285
0.062
0.785
2.216 *
2.686
53.140
0.274
108.852
4.267
4.365
1.195
11.383
2.004
8.264
6.867
0.000
0.212
6.196
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
o.ooc
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
1985
UNADj .
NOX
1985
UNAOJ.
voc
149.620 152.960
paTcrnov— unuMno T i c
Lrt 1 CuUK I — NUN MUD 1 Lt
1985 1985
UN ADJ. UN ADJ.
MCX
0.008
0.052
0.115
0.332
0.092
0.477
0.007
1.425
C.-d4
3.314
16.292
0.009
3.176
0.015
3.807
14.018
12.425
0.253
0.21S
0.733
23.612
0.087
0.000
0.006
0.143
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
-------
EMISSIONS (TONS/DAY)
10.36 MONDAY, MAY 2, 1989
NEDS STATE
DESCRIPTION
Cutback Asphalt Paving Oper.
Fugitives from SOCHI
Bulk Terminals and Bulk Plants
Petroleum Refinery Fugitives
Process 3ms. - Baker: ?s
Process Ems. - Pharm. Mfg.
Crude Oil/Nat.Gas Prod. Fields
Hazarccus Waste TSDFs
COOE =
sec
101
102
103
104
•C5
106
"CS
1C9
=west virgim
1985
uMADj.
CO
0.000
0.000
0.000
0.000
-j.CCO
0.000
o.ooc
0 . 000
i a UAitiiU
1985
UNADJ.
NOX
0.000
0.000
0.000
0.000
0/JOO
0.000
0.000
0.000
KT=NUNMU01Lt
1985
urJAD J .
VOC
2.800
31.600
9.000
2.400
1.000
0.200
10.600
247.600
1985 FULLY
AOuJSTcD
CO
0.000
0.000
0.000
0.000
1.000
Q.COO
o.coo
> ">OO
•j . j JU
1985 FULLY
AO JLiSTEu
NOX
0.000
0.000
0.000
0.000
3. 000
0.000
0.000
O.OCQ
1985 FULLY
ACjuSTcu
VOC
2.800
31.6CO
11.600
2.400
1.000
0.20C
•13.600
297. IOC
241.199
81.410
462.100
246.005
81.500
530.600
-------
EMISSIONS (TONS/DAY)
10.36 MONDAY, ,1AT c, i'?3? A-v
Nbos :
DESCRIPTION
Fixed Roof Tanks - Crude Oil
Fixed Roof Tanks - Gasoline
EFR Tanks - Crude Oil
EFR Tanks - Gasoline
Terephthalic Acid Mfg.
SOCMI Fugitives
Petroleui) Refinery Fugitives
Styrene-Butadiene Rubber Mfg.
Propylene Mfg.
Polyethylene Mfg.
Ethylene Mfg.
Petr. Refinery WW Treatment
Ptr. Refinery Vacuum Distil.
Carbon Black Mfg.
Automobile Surface Coating
Beverage Can Surface Coating
Coke Oven Byproduct Plants
Iron/Steel Blast Furn., Sinter.
Pulp/Paper - Recovery Furnace
Util. Ext. Comb. - Coal
Utit. Ext. Comb. - Oil
Util. Ext. Comb. - Natural Gas
Comm./Inst. Comb. - Oil
Ind. Ext. Comb.- Oi l,>10CMMBtu/h
Ind. Ext. Comb.- Gas,>100MMBtu/h
Ind. Ext. Comb.- Gas,<100MMBtu/h
>TATE C(
POD
4
5
6
7 "
17
19
20
22
23
24
25
26
27
32
33
34
39
41
42
50
51
52
59
87
88
90
jufc=untano
1985
UN ADJ.
CO
1112.860
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
148.060
386.420
2.080
0.000
4.790
0.010
8.950
8.430
0.540
0.010
0.000
0.360
0.360
0.000
CAI fclj
1985
UNAOJ.
NOX
84.060
0.000
0.000
0.060
0 . 300
0 . OCO
0.000
o.coo
0.000
0.000
0.000
0.000
0.000
17.960
0.080
0.000
0.010
6.9CO
0.090
* 6.050
256.030
0.190
0.030
0.000
9.900
3.050
0.890
UKT=PUINI
1985
UNADJ.
VOC
160.300
0.700
0.890
5.740
2.730
5.540
O.OCO
0.470
12.450
0.080
3.500
0.670
12.660
24.240
11.990
0.130
0.300
7.310
0.000
0.000
1.120
0.150
0.000
0.000
2.920
0.120
0.040
1985 FULLY
AOJ'uSTED
CO
1112.860
0.000
0.000
0.000
0.000
0.000
O.OCO
0.000
0.000
0.000
0.000
0.000 .
0.000
148.060
386.420
2.080-
0.000
4.790
0.010
8.950
8.430
0.540
0.010
0.000
0.360
0.360
0.000
1935 FULLY
ADJUSTED
NGX
84.060
0.000
0.000
0.060
0.000
0.300
0.000
C.JOO
0-CiOO
O.COO
0.000
o.aoo
0.000
17.960
0.080
0.000
0.010
6.900
0.090
6.050
256.030
0.190
0.030
0.000
9.900
3.050
0.890
1985 FULLY
ADJUSTiO
VOC
160.300
0.700
0.890
5.740
:.73C
5.540
0.000
0.470
12.430
0.080
3.500
0.670
12.660
24.240
11.990
0.130
0.300
7.310
0.000
0.000
1.120
0.150
0.000
0.000
2.920
0.120
0.040
1672.860
385.300
253.790
1672.860
385.300
253.790
-------
EMISSIONS (TONS/DAY)
10. Jo MONDAY, MAY 3, ;?89 A-=2
DESCRIPTION
- '-- NEDS STATE CODE=Cnt2rio
DESCRIPTION
SCC
11100
11200
11300
11510
11520
11610
11620
11630
11640
12100
12200
12300
12510
12520
13100
13200
13300
13510
13520
14100
22100
22140
22210
22220
22230
22240
22250
22260
22270
23110
23120
23130
iw « -»VJ
23150
23260
25120
25210
25220
25310
1.
0.
41.
1985
UNADJ.
CO
1.360
0.110
0.060
.000
.000
.510
32.070
46.330
15.280
2.020
0.030
0.030
0.340
0.040
12.120
0.140
0.020
5.430
0.250
0.990
0.470
486.290
0.960
8.010
10.470
2.040
13.250
0.550
3.060
0.180
0.290
0.270
1.360
0.380
37.270
29.710
0.000
4.880
0.240
104.j00
UAI tU
1985
UNADJ.
NOX
586.389
iUKI=nUBll_C
1985
UNADJ.
VOC
1283.730
CArEGORY=NONMC3ILE-
1985
UNADJ .
NOX
9.278
0.540
0.220
3.649
0.035
0.188
0.091
C.568
0.509
10.110
0.163
0.122
1.377
0.458
48.483
0.543
0.061
15.202
0.977
10.948
6.501
14.535
0.009
22.016
27.287
7.279
61.058
1.399
10.730
0.807
0.146
0.113
0.004
0.001
0.048
35.422
1.393
11.638
3. 335
0.207
1985
UNADJ .
VOC
0.000
0.000
0.058
0.967
0.002
4.696
5.815
5.908
0.133
0.384
0.014
0.007
0.074
0.021
0.953
0.011
0.002
0.120
0.024
0.393
0.010
23.408
0.558
3.821
2.512
0.563
4.665
0.^46
0.735
0.063
0.157
0.102
0.069
0.013
5.182
6.309
T.060
2.512
0.044
54.538
1985 FULLY
ADJUSTED
CO
4779.380
1985 FULLY
ADJUSTED
CO
1.860
0.110
0.060
1.000
0.000
41.510
32.070
66.:30
15.280
2.020
0.030
0.030
0.340
0.040
12.120
0.140
0.020
5.430
0.250
0.990
0.470
486.290
0.960
8.010
10.470
2.040
13.250
0.550
3.060
0.180
0.290
3.270
1.360
0.380
37.270
29.910
0.000
4.880
0.240
104.100
1985 FULLY
AOoUSTED
NOX
586.389
1985 FULLY
ADJUSTED
NOX
9.278
0.540
0.220
3.649
0.035
0.188
0.091
;.3c8
0.509
10.110
C.163
0.122
1.377
0.458
48.483
0.543
0.061
15.202
0.977
10.948
6.501
14.535
0.009
22.016
27.287
7.279
61.058
1.399
10.730
0.807
0.146
0.113
0.004
0.001
0.048
35.422
1.393
11.638
3.385
j.^07
1985 FULLY
ADJUSTED
VOC
1283.730
1985 FULLY
ADJUSTED
VOC
0.000
0.000
0.058
0.967
0.002
4. 596
5.315
5.908
0.133
0.384
0.014
0.007
0.074
0.021
0.953
0.011
0.002
0.120
0 .'024
0.393
0.010
23.408
0.558
3.821
2.512
0.563
4.665
0.146
0.735
0.063
0.157
G.102
0.069
0.013
5.182
:.:-09
0.060
2.512
C.C44
3-. 535
-------
EMISSIONS (TONS/DAY)
10.36 MONDAY, -MAY 6. 1939 A-63
DESCRIPTION
STATt (
sec
27110
27111
27120
27130
27140
27150
27160
31300
31500
32100
33100
47100
47200
51000
52110
56GOO
57100
37200
57300
70000
71000
77000
78200
85100
85200
85300
;oDt=untano
1985
UN ADJ.
CO
0.000
0.000
0.000
0.000
0.000
0.000
0.000
3.320
0.000
35.040
2131. 640
2.170
5.580
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
LAI tb
1985
UN ADJ.
NOX
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.997
3.323
0.269
37.233
0.070
0.000
0.000
0.000
0.000
0.000
J.OOO
0.000
' 0.000
0.000
0.000
0.000
0.000
0.009
0.017
UKT=NUNMUBlLt
1985
UNADJ.
VOC
21.308
10.623
0.229
29.055
3.749
42.950
2.499
0.195
0.000
0.581
237.519
0.382
2.587
3.994
0.026
107.343
0.000
0.019
0.091
112.137
48.652
76.220
120.548
0.000
0.452
0.083
1985 FULLY
ADJUSTED
CO
0.000
0.000
0.000
0.000
n . JDO
0 . 000
0 . C-CO
3.:zo
o.oco
35.040-
2131.640
2.170
5.530
0.000
0.000
0.000
0.000
J.OGO
0.000
0.000
0.000
0.000
0.000
0.000
0.000
0.000
1985 FULLY
ADJUSTED
NCX
0.000
0.000
0.000
0.000
o.oco
0.000
C.CGO
C.997
3.323
0.269
37.233
O.C70
0.000
0.000
0.000
o.:so
0.000
o.coo
0.000
0.000
0.000
0.000
0.000
0.000
0.009
0.017
1985 FULLY
ADuOS i EO
VOC
21.308
10.623
0.229
29.055
~ ~/_c
42.960
2.499
0.152
O.CCO
0.581
337.519
0.332
2.587
3.994
0.026
107.343
0.000 .
O.J19
0.091
112.137
43.652
76.220
120.548
0.000
0.452
0.083
3062.160
400.512
927.292
3062.160
400.512
927.292
-------
EMISSIONS (TONS/OAT)
10.56 MONDAY, MAY 3, 1939
DESCRIPTION
POINT
MOBILE
NON-MOBILE
TOTALS
KCUIUNHL
1985
UNADJ.
CO
5082.546
34668.900
12252.326
lUIMLS
UNADJ.
NOX
8236.384
6761.922
2472.987
1935
UN ADJ.
VOC
2179.762
7829.720
11041.091
1935 ,:ULL;
ADJUSTED
CO
5082.546
41579.629
12488.709
,935 r:JLLY
ADJUSTED
MOX
8236.334
5714.966
2706.194
i 9o5 CU'LL .'
ADJUSTED
VOC
2179.762
10240.208
12563.383
52003.772
17471.293
21050.573
59150.884
16657.544
24983.353
-------
APPENDIX B
CARBON BOND IV SPECIES ASSIGNMENTS USED IN ROMNET
-------
APPi.NDIX B. CARBON BOND IV CLASS ASSIGNMENTS FOR COMPOUNDS USED IN THE ROMNET INVENTORY
w
I
OLE PAR TOL XYL FORM ALD2 ETHY 1 SOP NR METH MT1IL
-43105
43106
43107
43108
43109
43110
43111
43112
43113
43114
43115
43116
43117
43118
43119
43120
43121
43122
43123
43124
43125
43126
43127
43128
43129
43130
43131
43132
43133
43134
43135
43136
43137
Iboni.;rs of nexane
Isoni.;rs of Heptane
liiom.'.rs of Octane
I boil; :rs of lionane
It.orii,:rs of l-ecane
Isoni,:rs of lindecane
IsoiM^rs of bodecane
IbOri;,:rs of 'i ridecane
lt;on. :rs of , ,,-tradecane
Isoiii:rs of 1 entadecane
C- 7 .lyclopai af f ins
C- 8 i ; y c 1 o pa i a f f i n s
C-9 tiyclopai af f ins
Miut:,al Spiiits
L&ct t.l Spirius
Itionu.rs of hutene
Isanu rs of 1 antene
.IiiOin> rrf of 1 .mtane
Terp>.nes
C9 Oiefins
CIO i/lefins
C2 C, clohexi-.ne
C3 C,. clohexi, ,ie
C5 C , clohextnie
C4 S..bstitui ^d Cyclohexane
C5 Substituted Cyclohexane
C6 S..bstitui >:d (j^clohexane
Al i pi.ar ics
Parai fins ((.16-C34)
Pa. -a, fins/01 jfins (C12-C16)
C.li) i araffir,.;
CO P., raff in
Clu hranched Alkane
6.0
7.0
8.0
9.0
10.0
11.0
12.0
13.0
14.0
15.0
7.0
8.0
9.0
6.0 1.0
8.0
1.0 2.0
1.0 3 . n
5.0
1.0 8.0
1.0 7.0
1.0 8.0
8.0
9.0
11.0
10.0
11.0
12.0
1.0
25.0
0.5 13.0
10.0
9.0
16.0
-------
Ai'Pi.NDIX B. CARBON BOND IV CLASS ASSIGNMENTS FOR COMPOUNDS USED IN THE ROMNET INVENTORY
cu
to
OLE
43138
43139
43140
43141
43142
43143
43144
43145
43146
43147
43148
43149
43150
43151
43152
43153
43154
43155
43156
43201
43202
43203
43204
43205
43206
43208
43209
43211
43212
43213
43214
43215
43216
C-8
Pun:
C7-C
ca P
cy P
C.'i 0
C'j P
C'j P
Gil
C12
I som
C8H1
I som
Ifjoni
CJ21I
C101I
C/IJ]
'\ ton.
Is urn
Me l h
Etlia
Ethy
Prop
Prop
Ac at
Prop
Mei.h
3-i-lfc
n] ef ins
i fins (i 2-C7)
16
..raff in
,,raf f in:
i e t i n
. , r a f f i n
,raf f in/ Olef in
olefins
\i\ ef ins
,:rs Of C9H16
-',
,:rs Of MOM18
.:l-S Of i 11H20
:2
16
. rs of hepLadecane
rs of (.r. cadecane
iflci
..e
i ene
,,ll(3
. ne
^ l.ene
.di ene
) l.acetyl -Mie (Propyne)
i hyl-1-l'^ntene
1
1
0
1
1
1
1
1
1
1
1
.0
.0
.5
.0
.0
.0
.0
.0
.0
.5
.0
N-Iku ane
Bui.ei.e
Iso-
Js.
-------
AI'PIMDIX B. CARBON BOND IV CLASS ASSIGNMENTS FOR COMPOUNDS USED IN THE ROMNET INVENTORY
to
U)
43217
43218
43220
43221
43222
43223
43224
43225
43226
43227
43228
43229
43230
43231
43232
43233
43234
43234
43235
43238
43241
43242
43243
43245
43247
43248
43250
43252
43254
43255
43256
43257
43258
Ci s- .-Butent
1 , 3-i:utadiei,c:
N-Pe:.tane
I so Pent ane
2 , 2 himethy] p
3-Mei hyl-1-Latene
1-Pentene
2-Me. hyl-1-hiitene
Ti an..-2-Peni
Ci s-..-Pentei
2-flei hyl-2-h.Jtene
2- Me. hylpenl ane
3-He. hyl Pei.Lane
H e x a i . e
Hfc|jt..ric:
Ociai.e
2,1 himethyl
2 , J I. i methyl
Ncnai.e
N-i)e. ane
N-iJniier.ane
Cycli pentant
I so pi ene
1-He: ene
2 ,4-liirnethy]
Cy-:l i.iicxane
2 , 2 ,', -Trimec
2 , J , »', -Trimet
isropane
itene
itene
:ne
itene
ne
ane
1-Butene
1-Butene
entane
ylpentane
yl pentane
2.0
2.0
5.0
5.0 '
5.0
1.0 3.0
1.0 3.0
4.0 1.0
1.0 2.0
1.0 2.0.
1.0 3.0
6.0
6.0
6.0
8.0
5.0 1.0
1.0 4.0
9.0
10.0
11.0
5.0
1.0
1.0 4.0
7.0
6.0
8.0
8.0
8.0
12.0
0.56.0 1.5
1.0 8.0
13.0
-------
AIM'. NDIX B. CARBON BOND IV CLASS ASSIGNMENTS FOR COMPOUNDS USED IN THE ROMNET INVENTORY
OLE PAR TOL XYL FORM ALD2 ETHY I SOP
NR METH MTIIL
43259
43260
43261
43262
43263
43264
43265
43269
43270
43271
43272
43273
43274
43275
43276
43277
43278
43279
43280
43281
43282
43283
43284
43285
43286
43287
43288
43289
43290
43291
43292
43293
43294
N--TL.I radeca.,
N--P(-.iitadecai.
Meth/lcycloi.
Methy 1 cyclO(.
2-Mi.ihyl He..
H^pt .:r,e
Oc:ti;,ie
1 Nunene
3 Mi-.i hyl-T-.;
3,5, :.-Trimei
Mutli/lcycloj.
Cycl .ihexene
2,3 Dimethyl
2- He:, hyl-1, >
2,3 i nine thy I
2 , 4- Dimethyl
2 , 5- i'i methy i
2-Eu.yl.-l-B,,
2,3, ) Trimei
1- Bin yne
2- Bui yne
C-3-ilexene
2-Mui hyl-2-P
2-Hei.ene
Di miii hylhexi
2,2 nimethyi
EL hy i eyclohi.
Cc Diet7 ins
2 , 3 ui methy 1
2 , 2-i ii methyl
Cy,: 1 ..pen tent
4- Me i hyl-T- i
C7 OieEins
e
e
exane
entane
;,ne
-Pentene
hylhexane
en t-ene
Pentane
-Butadiene
butane
hexane
hexane
i ens
hyl pentane
dntene
ne
hexane
xane
hexane
butane
-Pentene
14
15
7
6
7
1.0 5
1.0 6
1.0 7
1.0 4
9
1.0 4
2
7
6
8
8
5
8
3
3
2
1.0 4
2
1.0 6
8
8
1.0 4
8
6
1
2
1.0 5
.0
.0
.0
.0
.0
.0 :
.0
.0
.0
.0
.0
.0 2.0
.0
1.0
.0
.0
.0
.0 1.0
.0
.0 1.0
.0 1.0
.0 2.0
.0
.0 2.0
.0
.0
.0
.0
.0
.0
.0 2.0
.1) 2.0
.0
-------
Al'PlUDIX B. CARBON BOND IV CLASS ASSIGNMENTS FOR COMPOUNDS USED IN THE ROMNET INVENTORY
to
I
OLE PAR TOL XYL FORM ALD2 ETHY
43295
43296
43297
43298
43299
43301
43302
43303
43304
43305
43306
43308
43309
43310
43311
43312
43313
43314
43317
43318
43319
43320
43321
43322
43330
43331
43332
43333
43334
43335
43336
43337
43350
3-ilc:i hylhex;.,ie
2-Mei hylhepi ane
4- Hei hylhepi ane
3-t-ltM hylhepi ane
1-i-Iei hylcycl ohexene
Meuhyl Alcol.ol
Ethyl Alcohi. I
N-I'vv.pyl Al( Jhol
Isj- I ropyl / I conol
N- ilui yl Alct.liol
Isob'.cyl Ale >>ho L
Buiiyi Cellos.) L ve
Terl- Butyl Alcohol
Mei.h; 1 Cellc. jolve
Ce i. 1 1. solve
2-(2 Butoxyei.hoxy)-Ethanol
l-ICtliOxy-2-Pi-opanol
S-liui yl Alcciiol
Cycli.hexanol
2-i-:tl.yl Hexa.iol
Pcnt..nol
Diaci.cone Al,:ohol
2-iiltl.yl-l-He.tanol
1 ,-'i luitanedi .>L
Is.)au yl Alcohol
Di iiioi hylpent iiiol
Dimei hylocta.iol
Dimei hylhept .mo'l
Me> li) Iheptan.ii
Mei hi.xyethox/cthanol
Oci aiiol
Bui o^ yethoxy nhanol
Dii.iel Dylethe,
7.0 :
8.0
8.0
8.0
1.0 5.0
1.0
0.4
1.5
1.5
4.0
4.0
6.0 1.0
3.0
3.0 1.0
2.0 „ 1.0
4.0 * 2.0
3.0 1.0
4.0
6.0
8.0
5.0
4.0 1.0
8.0
4.0
5.G
7.0
10. U
9.0
8.0
3.0 1.0
8.0
4.0 2.0
2.0
NR METH MTHL
1.6
1.5
1.5
1.0
-------
Ai'l'i.MDIX B. CARBON BOND IV CLASS ASSIGNMENTS FOR COMPOUNDS USED IN THE ROMNET INVENTORY
u>
I
OLE PAR TOL
43351
43367
43368
43369
43370
43371
43372
43373
43374
43375
43376
43377
43378
43379
43380
43381
43391
43392
43395
43396
43397
43399
43403
43404
43405
43407
43408
43409
43410
43430
43432
43433
43434
El lly 1
CM /(..,
Glyc..
Pi 0|.>
El hyi
Hfcxy I
Di bin
Diei i,
Dip!',;
Trie.
Meth/
Carbi
Me th/
Biicy I
Giy(...
Poly,.
2-Uui
Eliiy i
C7!lt .
ClOlli
Ti i m.
CSillu
Form i
Acoi i
Pi..pi
Ac ry I
Palrni
Ad i p i
Ether
1 Ethe.
1
1 ene Ci
ene -Gl\
ene Gly
yl Ethc
ylene ii
pylene
hylene
1 t-Bui
tol
1 Carbi
Carbi i
rol
thyleni
y Ltetr;.
f uran
0
60
thylcyc
0
c Acid
c Acid
onic Ac
i c Acid
tic Ac i
c Acid
He:,a jecanoic
Me i hi
Mfcilv,
En.y i
n-i'r>.
L Forma
1 ;,cetai
/•cetai
pyl Ace
ycol
col
col
r
1 ycol
Glycol
o 1 y c o 1
yl Ether
tol.
ul
Glycol
hydrof uran
1 ohexanol
id
.1
Acid
. e
, iltC:
2
0
0
1
0
6
6
2
4
2
3
2
3
4
1
2
6
2.0 2
1.0 5
1.0 8
9
5
1
2
1.0
15
4
15
1
2
3
4
.0
.4
.4
.5
.4
.0
.0
.0
.0
.0
.0
.0
.0
.0
. 3
.1)
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
.0
XYL FORM ALD2 ETHY
1.0
1.0
1.0
2.0
2.0
1.0
2.0
1.0
2.0
1.0
ISOP
1
1
]
i
1
i
1
1
1
1
2
1
1
]
1
1
NR METH MTII
.6
.6
.5
.6
.5
.0
.0
.0
.0
.0
.0
.0
.0
f)
.0
.0
-------
Al'Pl.riDIX B. CARBON BOND IV CLASS ASSIGNMENTS FOR COMPOUNDS USED IN THE ROHNET INVENTORY
43435
43437
43438
43440
43441
43444
43446
43450
43451
43452
43453
43454
43455
43456
43457
43458
43459
43460
43461
43462
43463
43464
43465
43466
43467
43468
43469
43470
43471
43472
43472
43473
43474
n-Bui yl Acei ate
Meth> 1 Aery ! ate
Et ny 1 Acryl.,t e
Buiyi Acryl<,ce
Methyl Methi.crylate
Isopropyl A( etate
Isobutyl Ace Late
DiiTteihyl Foiniamtde
It.oL..cyl Isc but/rate
Ctl.l .-solve i eetate
Vi ny i Acetai e
Mttib ; 1 Palmi cate
Me ib, 1 Myri i r. ate
Mei.h, 1 Steai .ite
Mer.h; lal
Suusi i.i:uted i.'9 Kster (C12)
C.S F...u:r
Me..!,, 1 Cll t..Ler
Mti:h, L C12 E:;cer
Mfci.h) L C13 E:iter
Mei.li) 1 C14 E.juer
Mti.lij 1 CIS E. ;cer
Me.h; 1 C19 tdter
Mei.h>l C20 E.Ler
C4 Si.bstitut :d Cyclohexanone
Is.jbi.cyl Acr /Lai. e
bm o, yi-.thoxj M.hhnol Acetate
Mc-i \\- L Dodec inoate
Di i.iei iiy lbutcinc;di oate
bin o: /butent
Di L,ei uylperit niedioate
ELI.y I iu;xanoa > e
Me* h) i inethyl j.ropenoate
OLE PAR
5.0
1.0 1.0
1.0 2.0
1.0 4.0
1.0 2.0
4.0
5.0
2.0
7.0
3.0
1.0 1.0
16.0
14.0
18.0
3.0
11.0
4.0
12.0
13.0
14.0
15.0
16.0
20.0
21.0
10.0
1.0 4.0
5.0
12.0
4.0
1.0 4.0
' 5.0
7.0
1.0 2.0
TOL XYL FORM ALD2 ETHY I SOP MR METH MTHL
1.0
1.0
1.0
1.0
1.0
1.0
1.0
1 .0
1.0
1.0 1.0
1.0
i .0
1.0
1.0
1.0
] .0
] .0
] .0
1.0
1.0
1.0
1.0
1.0
.1 .0
2.0 1.0
1.0
2.0
1.0
'1 . U
j ,0
] .0
-------
AI'PINDIX B. CARBON BOND IV CLASS ASSIGNMENTS FOR COMPOUNDS USED IN THE ROMNET INVENTORY
OLE PAR TOL XYL FORM ALD2 ETHY ISOP NR METH MT1IL
43475
43476
43477
43502
43503
43504
43505
43510
43511
43512
43513
43514
43515
43520
43551
43552
43559
43560
43561
43562
43563
43564
43565
43566
43567
43568
43570
43601
43602
43603
43604
43650
43704
Mfcthy
Di met
Di me i
Foriii.i
Ac.ei .,
Pi 0|J|
Ac co \
Bucy i
Isob,,
Hexa<.
Gl/Oi.
Meth;
CroLi..
To t n I
Ac.il',.
Meth,
Me ill;
Mei. li;
cya.'.
Mt.ih)
2-l'l.M
He,,,..
]>i,.U:i
Trim,
Ten-,
Mo. if.:,.
Alkci,
Ethyl
Prop',
Ma 1 t: i
Ac.-.-l i
Ox;-t!,
Ac.-y I
lethyljentanoate
hylhex, nedioate
hylpeni anedioate
Idehydt
Idehydt
onaldel.yde
ein
aldehyde
tyraldt hyde
al
al
1 Glyo>. al
naldehy Je
C2-C5 Aldehydes
ne
1 Ethyi Ketone
1 Butyj Ketone
1 Isobi. t yl Ketone
hexanor.o
1 Amyl iCetone
hyl-3-li Jjtanone
none
hylcyc 1 .)but anone
thylcyc 1 opentanone
intthyl pj:iit anone
one
e Keton.i
ene Oxi .Je
1 ene Ox i.de
c Anhydride
j Anhyd.'ide
. i h t e s
oniliri ! .:
7.0 J.O
6.0 2.0
5.0 2.0
1.0
1.0
1.0 1.0
1.0 1.0
2.0 1.0
2.0 1.0
4.0 1.0
1.0 1.0
1.0 1.0
1.0 1.0
1.5 1.0
3.0
4.0 "~
6.0
6.0
6.0
7.0
7.0
7.0
6.0
8.0
9.0
1.0 7.0
1.0 2.0
1.0 1.0
2.0 1.0
2.0
2.0 '2.0
1.0 1.0
-------
AI'PI.NDIX B. CARBON BOND IV CLASS ASSIGNMENTS FOR COMPOUNDS USED IN THE ROMNET INVENTORY
00
I
43721
43740
43776
43777
43778
43779
43780
43801
43802
43803
43804
43805
43811
43812
43814
43815
43817
43819
43820
43821
43822
43823
43824
43825
43835
43836
43837
43838
43839
43840
43841
43842
43843
Et hy i amine
Ti iriK:thylami ne
Hi. x a. .ie thy lei, edi amine
Et liai.olaminfj
Ethy 1 eneamines
Capri. lactam
Dimei hyl AKyl Amines
Methyl Chloj ide
Di chl orometl.ane
Ch 1 o, ot'orm
Garb, n Tetr;. chl oride
Me ill; lene Bi ,>mide
Tr i cl.lorof li.oromethane
Eruyi Chloride
1,1,1 -Trichl oro.ithane
Einyiene Dic.nLoride
Pe. «.:i Loroetl. /I ene
Me i li , \ ene Bi omi de
1,1, !:-Trich! .jroethane
Tt i c i.l urotri r Luo roe thane
Tr inu thylflu vroailane
Di i;h i oi-odif 1 > ID rume thane
Tr i cl.loroeth /lene
Mec h; lene Chi.oride
1-Chl orobuta.ie
3- (Cl, Lorometiiyl )-Hept;ane
Eidy i aiie Dib. i>mi de
IJr.)p) 1 ene Di .iiloride
Tei i .. f 1 uoroiii .ifhane
Cl'iioi >dif luoi omethane
Dii li i -)i-otetr . I luore thane
Ch i Oi .)|ientaf i uoroethane
Ile.^a i l uoroet iiane
OLE PAR
0.4
3.0
6.0
0.4
0.4
5.0
3.0
2.0
4.0
8.0
1.5
TOL XYL FORM ALD2 ETHY I SOP NR METH MTII
1.6
1.6
1.6
1.0
1.0
1.0
1.0
1.0
1 .0
] .0
I'.O
2.0
2.0
2.0
1.0
2.0
2.0
] .0
1.0
1.0
1.0
2.0
] .5
1 .0
] .0
2.0
'•0
2.0
-------
AI'PI.NDIX B. CARBON BOND IV CLASS ASSIGNMENTS FOR COMPOUNDS USED IN THE ROMNET INVENTORY
CD
43844
43845
43860
43862
43863
43902
43922
43933
43934
43950
43951
43952
45101
45102
45104
45105
45106
45107
45108
45109
45110
45111
45112
45113
45150
45201
45202
45203
45204
45205
45206
45207
45208
Ti i i i uoromei
Chlo.-otrif 1 1,
Vinyi Chlori
Chlui-oprene
E|.,ic hlorohyu
El liy i
Trim.
Curb,
Garb.
Octa,.
Si Lo,
Te c > .
Naphi
I t.orij>
Is on,
I son.,
Isom.
Tr i n'i.
I soin.
C3/C-.
CIO :
C10II i
1 tiUfil,
ci nit
ISoili,
Beuz.
To In.
Etliy i
o~Xy 1
m- X y I
p-Xyl
1,1,:.
1 , •-' , <
Mercaj
ithylfli,
,nyl Sul
>n Sulfi
iethylc)
.ane
.methyl :.
ha
rs of >
rs of 1
rs of 1.
rs of 1.
thylbei,
rs of 1
/C5 All
romat i<
2
rs of (
0
rb of t
ne
ne
benzene
ene
ene
ene
OLE
hane
oromethane
de
2.0
r i. n
can
orosilane
fide
de
clor.etrasiloxane
i lane
yiene
Lhyl toluene
,,cy 1 benzene
i et hylbenzene
t.ene.
.ropylbenze
/I benzenes
lOHJO 1 0.0
tOHl8 1 0.0
-Trimet uyl benzene
-Trimetnyl Ir.enzene
PAR TOL
3
2
2
1
8
4
8
1
3
2
1
2
3
3
2
3
8
1
1
1
1
.0
.0
.0
.0
.0
.0
.0
.0
.0 1.0
.0
.0
.0 1.0
.0 1.0
.0 1.0
.0
.0
.0
.0
1.0
.0 1.0
.0
.0
XYL FORM ALD2 ETHY ISOP NR METH MTU
1
1
1
1
1
1
1
1
1
1
1
1
1.0
1.0
1.0
1.0
1.0
.0
.0
.0
.0
.0
.0
.0
5.0
.0
.0
.0
.0
.0
-------
At'Pl NDIX B. CARBON BOND IV CLASS ASSIGNMENTS FOR COMPOUNDS USED IN THE ROMNET INVENTORY
w
I
45209
45210
45211
45212
45215
45216
45217
45218
45220
45221
45225
45226
45227
45228
45229
45230
45231
45232
45233
45235
45236
45237
45238
45240
45241
45242
45243
45244
45245
45246
45247
45248
45249
n-Pi .>pylben. ene
Cumene (Isorropyl Benzene)
o-Etliyltolui ne
m- Et ny 1 tolut ne
ten. -Butylbi nzene
s- 8ui.ylbenzi.ne
1,2 i»iethyll.enzene
m-0i,:thylbei:^ene
St yr :ne
Mtr.li/1 Styr, ne
1,2, ">-Trimei liyl benzene
Bi pliL.riyl
Mt:Lh-/r Biph. nyl
Ethyl Styrei.c
Di vi ,,y 1 Ben: cine
Di (Ei hylphei.yl) Ethane
Pent ) 1 Benzi ne
Di ph, nyl Eth-nie
Et liy i -Phenyl - Phunyl-Ethane
Bucyl Benzei.c
Di is..propyl lienzene
1,'2,),4 Teci jmethylbenzene
Et uy i toluene
Pro pi 1 benzer.c:
4-i'h. nyl-1-tiitene
T- l-i henylbi.iiene
Etiiyi dimeth) 1. benzene
Tei T;. methyl L.'nzi-ne
C5 -Ai kylbeni ,.'nes
C5 -Ai kylben^.tnes (Unsat.)
C6 -AI kyl benzene
C4 -Ai kylstyi ..-lies
C7 A i kyl ben2>:ne
OLE PAR
2.0
2.0
1.0
1.0
' 2.0
3.0
2.0
2.0
0.5
1.0
1.0
1.0 1.0
1.0
4.0
4.0
1.0
3.0
4.0
2.0
1.0
2.0
1.0 1.0
1.0 1.0
2.0
2.0
4.0
1.0 2.0
5.0
1.0 3.0
6.0
TOL
1.0
1.0
1.0
1.0
1.0
1.0
1.0
1.0
2.0
1.0
2.0
1.0
1.0
1.0
1.0
1.0
1.0
1.0
1.0
1.0
1.0
XYL FORM ALD2 ETHY I SOP NR METH MTI1L
1.0
1.0
1.0
1.0
1.0
1.0
5.0
1.0 5.0
1.0
1.0
1.0
1.0
1.0
1.0
1.0
-
-------
Al'Pl iJDIX B. CARBON BOND IV CLASS ASSIGNMENTS FOR COMPOUNDS USED IN THE ROMNET INVENTORY
45250
45300
45301
45302
45303
45304
45310
45311
45320
45330
45401
45402
45403
45404
45450
45451
45452
45454
45455
45456
45470
45477
45501
45502
45503
45550
45601
45604
45605
45610
45701
45702
45703
C.j -Al kylstyi ene
Phcii,,l
Nony i phenol
Et liy i dimeth) i. phenol
C'fAl K.ylphei.,)l s
C5- A i kylphei'Hil s
C8 1'l.enols
C9 Pl.enols
Di Hiet hylben; y lal cohol
Bi phi.iiylol
XyLei.e Base Acids
Benzole Acid
Tere| htihalic Aci d
Diinei hyleth) 1 benzoicacid
Dimethyl Tei ^phthalate
Dimei Ivyl Phi iialate
Di oui yl Phtl..ilai:e
Dipr.pyl Phtiidlate
BuLyl Benzotii.e
Bunyi i sopro].ylplithalate
Di--C(, Alkyl iMithalate
Bui.yl benzyl]. litihalate
Bfcuz.. I ilehyde
p-'i'oi .ialdeh>.U:
2-l''in fural
Met h; lacetopiionone
Phi h<. 1 i c Anh /.lr i de
Fui ti.iryl Alcohol
Cr^Si. 1
Cl'IHi40
AM i 1 i lie
Ni i. n Dcnzene
'!,,'. i. ii. hloro,. 1 1 1 oaniline
OLE PAR
1.0 2.0
1.0
8.0
2.0
3.0
4.0
1.0
2.0
1.0
1.0
1.0
2.0
3.0
3.0
9.0
7.0
5.0
8.0
17.0
5.0
1.0 1.0
1.0
1.0
2.0 1.0
2.0
1.0
1.0
1.0
TOL XYL FORM ALD2 ETHY I SOP NR METH MTU
1.0
5.0
1.0
1.0
1.0
1.0
1.0
1.0
1.0
1.0 5.0
1.0
6.0
7.0
1.0 1.0
7.0
7.0
7.0
7.0
6.0
7.0
7.0
1.0 7.0
1.0 5.0
2.0 4.0
1.0
1.0 1.0
7.0
1.0
1.0 1.0
!).0
5.0
b.O
-------
AlPI iJDIX B. CARBON BOND IV CLASS ASSIGNMENTS FOR COMPOUNDS USED IN THE ROMNET INVENTORY
I
LO
45704
45705
45706
45730
45731
45732
45740
45750
45801
45805
45806
45807
45808
45810
45830
45831
46102
46103
46110
46111
46112
46114
46115
46201
46202
46203
46204
46210
46601
46602
46701
46702
46703
OLE PAR TOL XYL FORM ALD2 ETHY ISO
Bronu.dinitrc.anil ine
Broniudini tr<- benzene
n- I'hi.nylani 1 i ne
Mer.h; lene(B Ki-Phenyli s
T(jlu...ne Dii:ocyanate
Tolu..neisocyanide
Total Aromatic Amines
Pi pei ylene
CLLo. olienzei.if
o-Di. hlorobt uzene
m-l)i. hlorobi nzene
p- i)i , hi orobt nzene
Di oh i orobem .anes
Benz/1 Chloi ide
Trici.lorobei^enes
Teur.;chlorol >;nzenes
Anihi aquinoi.^
An: in. anthrac,.) inone
Mer.h, Unebis (C61I4NCO)
4 , 4-Mer.hyler,c2 Di aniline
Plujn ; 1 I soc) anai.e
4 -ilai riylanil i ne
Diuiei hylnaphi hyi idine
Di iiy.i roxynaj \ halenedione
Oci al.ydroind.:neb
Me i In xynaphl ualone
Di iiyu roxynaj i lial enedione
Ct .:(j..al. e
Te i r, iiii: thyl t ii i ourea
Be.^i lliiazol :
Na|>Ll.a 1 ene
Meih^l Napht u.-jl^nes
Dimei hyl 'Nap. lial ene
1.0
1.0
1.0
1.0 '
1.0
1.0
1.0
2.0 1.0
1.0
1.0
1.0
1.0
1.0
1.0
1.0
1.0
2.0
2.0
1.0 1.0
1.0 1.0
1.0
1.0
3.0 1.0
2.0 1.0
9.0
3.0 1.0
2.0 1.0
1.0 1.0
4.0
2.0
2.0 1.0
3.0 1.0
4.0 1.0
NR METH MTHL
1.0
5.0
5.0
5.0
5.0
5.0
5.0
5.0
5.0
12.0
12.0
7.0
5.0
6.0
3.0
1.0
5.0
-------
Al'i'i NDIX B. CARBON BOND IV CLASS ASSIGNMENTS FOR COMPOUNDS USED IN THE ROMNET INVENTORY
46704
46705
46706
46707
46708
46709
46710
46711
46712
46713
46714
46715
46716
46717
46718
46719
46720
46721
46722
46723
46724
46725
46726
46727
46728
46729
46730
46731
46732
46733
46734
46735
46736
Pi i ei i y 1 na ph. 1 1 1 a I ene s
Ai:i-jii..phthyli';iie
Ai.^i...phtheru:
Fl jo, ene
Pliijiiiiiithrent:
Am. In acene
Fl no i anthem;
C2 Alkyl InUan
Inciijiie
Py rene
Benzo(g,h,i ) FLuoranthene
Chry^ene
Benzo (a) Anthracene
Benn.) (b) Fi ..icranthene
Bc-.nz,) (k) F) uoranthene
Beni:,, (A) P>rene
In.lf!,.o( 1 ,2 , J-cd ) Pyrene
Ben/:,, (g,h,i) Perylene
Dibenzo(a,h) Anthracene
Pery i ene
Benz,. (e) Pj renc
Anr.h,,ni:hren£
Coroi.ane
Methyl -Anthracenes
Mechyl-Phenanchrenes
C2--A1 kyl-Ant hracenes
C2 -A! kyl-Phenanchrenes
Cycl open ta-Ant hracenes
Cyclupenta-Phenanthrenes
Meuhy 1-F1 uoranthene s
Cycl(,penta(c ,d)Pyrene
Ben2i;(c )Phen jnthrene
Mei. hy L-Benza.tLhracenes
OLE PAR
1.0
1.0
1.0
1.0
1.0
3.0
0.5
1.0
1.0
1.0
1.0
1.0
1.0
2.0
2.0
3.0
3.0
3.0
3.0
1.0
2.0
1.0
TOL
1.0
1.0
1.0
1.0
1.0
1.0
1.0
1.0
1.0
1.0
1.0
1.0
1.0
1.0
1.0
1.0
1.0
1.0
1.0
. 1.0
XYL FORM ALD2 ETHY I SOP
1.0
1.0
1.0
1.0
1.0
1.0
1.0
1.0
1.0
1.0
1.0
1.0
1.0
1.0
1<0 --
1.0 ""
1.0
1.0
1.0
1.0
1.0
1.0
1.0
1.0
1.0
1.0
1.0
1.0
1.0
1.0
1.0
1.0
1.0
NR METH MTI!
2.0
3.0
5.0
h.O
5.0
1.0
1.0
3.0
3.0
3.0
5.0
5.0
3.0
4.0
6.0
6.0
5.0
3.0
y.o
0.0
5.0
5.0
5.0
5.0
5.0
5.0
1 .0
1.0
3.0
3.0
-------
Al'Ph.NDIX B. CARBON BOND IV CLASS ASSIGNMENTS FOR COMPOUNDS USED IN THE ROMNET .'INVENTORY
I
01
46737
46738
46739
46740
46741
46742
46743
46744
46745
46746
46747
46748
46749
46750
46751
46752
46753
46754
46755
90001
90002
90003
90004
90005
90006
90007
90008
90009
90010
90011
90013
90014
90015
Mocli/l-Benz) henanthrenes
Meth>'l-Chryi,enes
C2 -A i kyl-Bei.zanthracenes
C2-Ai kyl-BeiiZOphenanthrenes
C2-Alkyl-Chi ysenes
Benz.>pyrene;;
Di benzanthracenes
Di be,.zphenaiithrenes
Di be.izopyrei.es
C2-A i kylnapi halene
Mfcth /I indan:. •
Mtth/ldecal i ns
Meth/ldihydi onaphthalene
Dimei hylind«,as
Dihy.lronaptl.alene
Diniet hylindi ne
Deca i ins
Etny i indan
Tr im.,thylindan
Dodecene
2,3, ',-Trimet hylhexane
2,4 himethylheptane
3,5 himethylheptane
2,5 himethylheptane
2,3 himethylheptane
4-Mei hyl-1-Fantene
2-ilei hyloctane
2,4, !.-Trimet nyl heptane
m-Xylene and p-Xylene
Met h^ lallene
C-''-<>ctene
l-he< ene
3-llei hylocta.ie
OLE PAR
1.0
1.0
2.0
2.0
2.0
1.0
1.0
1.0
1.0
4.0
2.0
11.0
3.0
3.0
2.0
1.0 1.0
10.0
3.0
4.0
1.0 10.0
9.0
9.0
9.0
9.0
9.0
1.0 4.0
9.0
10.0
1.5 1.0
4.0
1.0 8.0
9.0
TOL XYL FORM ALD2 ETIIY 1SOP NR METH MTHL
1.0 1.0 3.0
1.0 1.0 3.0
1.0 1.0 3.0
1.01.0 :i . 0
1.0 1.0 3.0
1.0 1.0 3.0
1.0 1.0 6.0
1.01.0 6.0
1.0 1.0 fc.O
1.0
1.0
1.0
1.0
1.0
1.0 *
1.0
1.0
1.0
2.0
-------
Ai-1'l.-.NDIX B. CARBON BOND IV CLASS ASSIGNMENTS FOR COMPOUNDS USED IN THE ROMNET INVENTORY
1^
o-.
90016
90017
90019
90020
90021
90022
90023
90024
90025
90026
90027
90028
90029
90030
90031
90032
90033
90034
90035
90036
90037
90038
90039
90040
90041
90042
90043
90044
90045
90046
90047
90048
90049
4-Mfcihyloctane
Mechylcyclo(,ctane
C6HH>03Si3
C8H2.,04Si4
Menli/1 propai.ci
MeUi) Ipropei.i
Mcch)Ibutent
Mechylbutadiane
Mfei;h t -Ipentei.c!
Methyl pentai.e
Mei:hj Icycloj.e
Mei h> Ihexanc:
Me i. hy 1 hexenc-s
Hexa.ieeane
n-ile, cadecar,.;
l-lln.i&oene
Cy;:li.pentyl< y
t-L'-lionene
N-Pei.tene
Pentne
ciu-J,4 Dn
MeihyIhexadi one
Mei.hy Lcycloh,;
t-3-liiixene
Merhy LhexanaI
Meihy Iheptyn.;
Merhy IheptaiK.'
Met.hy LcyclolK;xene
Meihy Lnonane
Mei h>-1 decant
Mei hy I undecai.e
OLE PAR TOL XYL FORM ALD2 ETHY 1SOP NR METH MTIIL
18
: C a n e
i
:ne
:S
mtadiene
clopentane
hylcyclohexane
ne
niniane
xaciiene
xene
e
9.0
9.0
6.0
8.0
4.0
1.0 2.0
1.0 3.0
2.0 1.0
1.0 4.0
6.0
1.0 2.0
7.0
1.0 5.0
16.0
17.0
1.0 9.0
10.0
5.0 2.0
1.0 3.0
4.0 1.0
5.0 1.0
8.0
1.0 1.0 2.0
7.0
1.0 1.0 2.0
2.0 2.0
5.0 1.0
7.0 1.0
8.0
1.0 5.0
10.0
11.0
12.0
-------
At'PLNDIX B. CARBON BOND IV CLASS ASSIGNMENTS FOR COMPOUNDS USED IN THE ROMNET INVENTORY
90050
90051
90052
90053
90054
90055
90056
90057
90058
90059
90060
90061
90062
90063
90064
90065
90066
90067
90068
90069
90070
90071
90072
90073
90074
90075
90076
90077
90078
90079
90080
90081
90082
Campi.ene
My rd:ne
b- Plu-llandrc ne
d- Limonene
Pent i. nyne
Pent ) Icyclohexane
Hfcxei.e
1- lle^tene
Hexw iienal
Hfcpt .dienal
Di me* hylbutc.ne
DJ inei hylbuti i.e
Di inet hylpeni ane
Dimei hylpent ane
Dimei hylcycl opentane
Dimei hylcycl opentenes
Nonadiene
Diinei hylhexsnes
Dimei hylhexadieue
Dimei hylethy Lcyclohexane
Diinei hyloctinies
Dirnei hylundc-cane
Methylpropyl cyclohexanes
Melhylisopropylcyclohexane
Diinei hyldecane
Et hy 1 octene
Dime! hylnona.ies
Ecliy I octane
Etliy i pentene
Etliy! cycloptiitene
Etliy I methylc /cl opentane
Etliy I hexane
Ethyl niethylli,:xaue
OLE
1.0
3.0
2.0
1.0
1.0
1.0
1.0
1.0
1.0
1.0
1.0
1.0
1.0
1.0
1.0
1.0
1.0
PAR TOL XYL FORM ALD2 ETHY I SOP NR METH MTH
8.0
4.0
6.0
4.0 2.0
2.0 1.0
11.0
4.0
5.0
2.0
1.0 2.0
6.0
4.0
7.0
5.0
7.0
5.0
3.0 2.0
8.0
2.0 2.0
10.0
10.0
13.0
10.0
10.0
12.0
8.0
11.0
10.0
5.0
5.0
8.0
8.0
9.0
-------
ArPHJniX B. CARBON BOND IV CLASS ASSIGNMENTS FOR COMPOUNDS USED IN THE ROMNET INVENTORY
OLE PAR TOL XYL FORM ALD2 ETMY '1SOP dR METH MTHL
90083
90084
90085
90086
90087
90089
90090
90091
90092
90093
90094
90095
90096
90097
90098
90099
90100
90101
90102
90103
90104
90105
90106
90107
90108
90109
90110
90111
90112
90114
90115
90116
90117
El.hy i methyli /c 1 ohexane
El hy i htjptam.
El hy i methyli.cLane
Ethyl bicycli.hepi.ane
Et. iiy i d i methy I peiitane
Et iiy 1 dimeth) Lcyclohexane
Euhy i propylcycluhexanes
Tei.r.i me chyle yclobutene
Tt i iiu. thylpeiiLane
Tt i nu.lhylpeiiiadiene
Tr inib c hy 1 he |i Lanes
Tr i mi.. thylhe>,^ne
Tr ) nu. thyloci .iney
Tt im. . i. hyldei .me
Tei rsiinethyli /clopentane
Oci.ai ri ene
No.ieiie
Bury i cyclohi: ;:ane
Merhylpropyl iionane
Penr.adiene
Meuhyloctaned
Propunylcycl ohexane
Met.hy Lnonene
Mei.hy Ldecene
Methy Idodecane
Propy Ihepten.js
Diutli/lmethy 1 cycl ohexanes
Isupi opylmei. hylcyclohexane
Dimei liyloctyne
Diinei liylbuty I cyclohexane
Tr i iru nhylhex .iiiej;
Isi>pi opylcyc 1 opentane
Li inoi.^rie
9.0
9.0
11.0
9.0
9.0
10.0
11.0
1.0 6.0
8.0
2.0 4 . 0
10.0
1.0 7.0
11.0
13.0
9.0 ..
2.0 ' ' 2.0
1.0 7.0
10.0
13.0
2.0 1.0
9.0
1.0 7.0
1.0 8.0
1.0 9.0 :
13.0
1.0 8.0
11.0
10.0
9.0 . 1.0
12.0
9.0
8.0
1.0 4.0 2.0
-------
Ai'Pi NDIX B. CARBON BOND IV CLASS ASSIGNMENTS FOR COMPOUNDS USED IN THE ROMNET INVENTORY
90118
90119
90120
90121
90122
90123
90124
90125
90126
90127
90128
90129
90130
98033
98034
98035
98040
98041
98044
98054
98056
98057
98058
98059
98060
98062
98063
98082
98083
98090
98091
98106
99908
OLE PAK TOL XYL FORM ALD2 ETHY 1SOP
Oc tai.ydropei.cal ene
Mfctliy 1 indent.
Prop-, Icyclol.iixane
Mel.lv, lethyll.eptane
TeCr..methyll,exane
Trim.:thylnoi,ene
Dimei hyloctMie
Hcne i cosane
Ei>;o.-.ane
Nona.iecane
Isop.opylcyt 1 ohexane
Et. iiy i d imeth) 1 octane
Gary* phyllei..i
2,2, !>-Trimer nylhexane
t-2-iiexene
C-2-nexene
2-Mei hyl-l-l'c;ntene
3-lle(.Lene
Indai.e
2,4 ,4-Trimet hyl-1-Pentene
Isoviileraldeliyde
Ethyl cyclopeutane
Tri methyl eye l.opentane
Dimei hylcycl ohexane
Tr imu: thylcyc I ohtxanes
Dictl.ylcyclchexane
N-1'ei.cylcycl .ihexane
Ethyl heptene
Tri.mi ihyldet..-ne
Mei hy 1 hepten,:
Dimei hylhept mes
Ethyl i iioprop/l Fither
2 , i I'imethyl.-ctane
1.0 1.0 1.0
1.0 1.0
9.0
10.0
10.0
1.0 10.0
1.0 8.0
21.0
20.0
19.0
9.0
12.0
3.0 9.0
9.0
2.0 ^ 2.0
2.0 * 2.0
5.0 1.0
3.0 2.0
1.0 1.0
7.0 1.0
3.0 1.0
7.0
8.0
8.0
9.0
10.0
11.0
1.0 7.0
1.0 11.0
1.0 6.0
9.0
3.0 1.0
10.0
NR METH MTHL
-------
Ai'Ph.NDIX B. CARBON BOND IV CLASS ASSIGNMENTS FOR COMPOUNDS USED IN THE ROMNET INVENTORY
I
M
o
99909
99910
99911
99912
99913
99915
99916
99917
99918
99933
99999
CAR BOM
OLE
PAR
TOL
XYL
FORM
ALD2
ETHL
I SOI1
NR
METH
MTHL
OLE
2,6 Dimethyl octane
2,4 l>i methyl octane
3, A Dimethyl octane
1-Mei hyl-3-l' rhylbenzene
1-Hei hyl-2-Lthyibenzene
Isobntylben:: ane
1-Mei hyl-3N- Propylbenzene
1-Mei hyl-3-J sopropylbenzene
2-Mei hyldecfuie
Denai urant
Unidentified
BOND iv CLAS<; DESCRIPTIONS:
PAR TOL XYL FORM ALD2 ETHY I SOP NR METH MTU
10.0
10.0
10.0
1.0 1.0
1.0 1.0
3.0 1.0
2.0 1.0
2.0 1.0
11.0
4.0
6.0
--- ol,.fi.n grc.up, two carbons connected by a double bond
— Pa. af f irii( , or saturated, carbon
-- To 1 uene gi jiip
- - Xy 1 ene gro.jp
--- i-'oi maldehy.Je molecule
— Oil.er aldehyde group, -(HC=0)
— ICLi.ylene n.alecule
-- iSwprene n.ilecule
— Uonreactive carbon (one carbon wi
— Mei hane molecule
— Mei hanol iinilecule
group (one carbon with associated hydrogens)
th associated hydrogen, chlorine, etc.)
-------
APPENDIX C
CHANGES MADE AS A RESULT OF CO QUALITY CONTROL
-------
TABLE C-l. CHANGES TO CO EMISSIONS
State
08
20
20
20
20
36
36
36
36
36
36
22
30
30
30
30
30
30
30
48
48
48
48
48
48
48
48 .
48
48
48
48
48
48
48
-tb
39
39
50
County
0180
0277
0907
1125
1205
0080
5740
1720
6400
7100
7100
1291
0140
0140
0140
0440
0440
0140
0140
0100
0100
0580
1580
1580
1580
1580
1580
1660
1660
1660
1800
2500
2500
2720
->^ou
3080
2940
0720
Plant
0010
0138
0023
0027
0020
5006
5003
5008
5008
5015
5015
7654
0002
0002
0002
0032
0032
0002
0004
0003
0003
0095
0006
0006
0006
0006
0006
0001
0001
0001
0010
0003
0003
0004
uGG4
0004
0005
0002
Point
07
06
02
04
03
13
01
99
16
03
04
02
02
07
10
02
05
08
01
06
08
20
06
07
08
12
14
05
09
11
02
03
21
06
Uo
14
11
1. 1
Revised CO
emissions
(TPY)
9,36.3
573
857
1,773
851
12,789
2,286
235
58,081
22,610
26,135
4,380
3,617
1 18
1.-312
1,981
1,050
593
1,957
25
2,697
11,159
855
974
2,018
15
11
625
13
1,876
1,910
1,986
18
2,468
ood
12
734
19.072
Estim-
ation
method
2
5
3
3
3
5
3
3
3
2
2
3
5
5
5
1
1
5
1
5
5
5
5
5
5
5
5
5
5
5
5
5
5
5
5
4
4
i
Action
Change
Change
Change
Change
Change
Change
Change
Change
Change
Change
Change
Change
Change
Change
Change
Change
Change
Change
Change
Change
Change
Change
Change
Change
Change
Change
Change
Change
Change
Change
Change
Change
Change
Change
Change
Change
Change
P }•} a J-J rr 0
Notes
A
A
A
A
A
A
A
A
A
A
A
A
A
A
A
A
A
A
A
A
A
A
A
A
A
A
A
A
A
A
A
A
A
A
A
A
A
D
NOTES:
"A" indicates changes made to the NAPAP, NEDS, and ROMNET
inventories.
"B" indicates the changes made to only the NAPAP and ROMNET
inventories .
C-1
-------
TABLE C-2. OTHER CHANGES
State
08
08
20
36
36
30
30
30
30
50
50
NOTES:
"A"
County
0180
0180
0907
7100
7100
0140
01AO
0140
0140
0620
0620
. .
Plant
0010
0010
0023
5015
5015
0002
0002
0002
0002
0001
0001
Point
07
07
02
03
04
02
07
08
08
36
36
Annual Maximum
operating hourly
SCC code rate rate
10200603
30103503 »x
30700104 155,844
30100503 25,000
30100503 35,000
10200901
10200907 342,000
30700401
30700104 108,000 14.0
30300199
30300101
~ t. n t- U ~ \IADAD MCTlC J n f\kA
Action
Delete
Add
Change
Change
Change
Delete
Add
Delete
Add
Delete
Add
MC"T*
Notes
A,B
A,B
A
A
A
A
A
A,B
A,B
B,C
B,C
inventories.
"B" indicates addition/deletion pairs. These are instances where a
source was deleted from the inventory but then reentered with a
different SCC.
"C" indicates the changes made to only the NAPAP and ROMNET
-------
APPENDIX D
COMPOSITE MOBILE SOURCE EMISSION FACTORS FOR DIFFERENT TEMPERATURES
-------
APPEND.! A D. COMPOSITE MOBILE SOURCE EMISSION FACTORS FOR DIFFERENT TEMPERATURES
Emissions
Year
1985
1985
1985
1985
1985
1985
1985
1985
1985
1985
1985
1985
1985
1985
1985
1985
1985
1985
1985
1985
1985
1985
1085
1985
1985
1985
1985
1985
1985
1985
Mean
dai Ly
teriip .
OF)
40
40
40
40
40
45
45
45
45
45
5U
50
50
5o
50
55
55
55
55
55
60
60
60
60
60
65
65
65
65
65
(g/mile)
VOC
Range
(F)
0
10
20
30
40
0
10
20
30
40
0
10
20
30
40
0
10
20
30
40
0
10
20
30
40
0
10
20
30
40
Total
3.811
3.822
3.825
3.829
3.835
3.747
3.759
3.774
3.780
3.830
3.677
3.801
3.717
3.777
3.822
3.613
3.638
3.687
3.762
3.875
3.566
3.624
3.699
3.791
4.006
3.562
3.624
3.726
3.911
4.224
Evapo-
rative
2.181
2.192
2.195
2.199
2.205
2.177
2.189
2.204
2.210
2.260
2.167
2.191
2.207
2.267
2.312
2.163
2.188
2.237
2.312
2.425
2.166
2.224
2.299
2.391
2.606
2.212
2.274
2.376
2.561
2.874
Gas
exhaust
1.486
1.486
1.486
1.486
1.486
1.426
1.426
1.426
1.426
1.426
1.366
1.466
1.366
1.366
1.366
1.306
1.306
1.306
1.306
1.306
1.256
1.256
1.256
1.256
1.256
1.206
1.206
1.206
1.206
1.206
Diesel
exhaust
0.144
0.144
0.144
0.144
0.144
0.144
0.144
0.144
0.144
0.144
0.144
0.144
0.144
0.144
0.144
0.144
0.144
0.144
0.144
0.144
0.144
0.144
0.144
0.144
0.144
0.144
0.144
0.144
0.144
0.144
NOx
3.91
3.91
3.91
3.91
3.91
3.84
3.84
3.84
3.84
3.84
3.78
3.78*"
3.78
3.78
3.78
3.72
3.72
3.72
3.72
3.72
3.66
,3.66
3.66
3.66
3.66
3.60
3.60
3.60
3.60
3.60
CO
21.18
21.18
21.18
21.18
21.18
20.25
20.25
20.25
20.25
20.25
19.38
19.38
19.38
19.38
19.38
18.56
18.56
18.56
18.56
18.56
17.80
17.80
17.80
17.80
17.80
17.09
17.09
17.09
17.09
17.09
Breakdown of evaporative
emissions
MOBILE 3.9
evapo- Running
ration loss
1.380
1.390
1.390
1.390
1.390
1.370
1.380
1.390
1.390
1.430
1.350
1.370
1.380
1.4 30
1.460
1.330
1.350
1.390
1.450
1.540
1.310
1.360
1.420
1.490
1.670
1.320
1.370
1.450
1.600
1.860
0.013
0.014
0.017
0.021
0.027
0.019
0.022
0.026
0.032
0.042
0.029
0.033
0.039
0.049
0.064
0.045
0.050
0.060
0.075
0.097
0.068
0.076
0.091
0.114
0.148
0.104
0.116
0.138
0.173
0.226
Excess
evapo-
ration
0.788
0.788
0.788
0.788
0.788
0.788
0.786
0.788
0.788
0.788
0.788
0.788
0.788
0.788
0.788
0.788
0.788
0.788
0.788
0.788
0.788
0.788
0.788
0.788
0.788
0.788
0.788
0.788
0.788
0.788
-------
APPENDIX; D. COMPOSITE MOBILE SOURCE EMISSION FACTORS FOR DIFFERENT TEMPERATURES
F
Emissions
Year
1985
1985
1985
1985
1985
1985
1985
1985
1985
1985
1985
1985
1985
1985
1985
1985
1985
1985
1985
1985
1985
1985
1985
1985
1985
1985
1985
1985
1985
1985
Mean
daily
t eni|) .
(f)
70
70
70
70
70
75
?:>
TJ
75
7!)
fao
80
8u
8(1
80
8i)
85
85
85
85
90
90
90
90
90
95
95
95
9'j
9!>
(g/mile)
VOC
Range
(F)
0
10
20
30
AO
0
10
20
30
AO
0
10
20
30
AO
0
10
20
30
AO
0
10
20
30
AO
0
10
20
30
AO
Total
3.576
3.665
3.799
A. 122
A. 612
3.610
3.738
3.989
A. 470
5.272
3.806
3.990
A.A18
5.211
6.627
A. 079
A. 356
5.10A
6.522
9.186
A.A6A
A. 965
6.325
9.092
9.735
5.022
5.986
8.831
9.6A8
10.588
Evapo-
rative
2.266
2.355
2.A89
2.812
3.302
2.350
2.A78
2.729
3.210
A. 012
2.A76
2.660
3.088
3.881
5.297
2.679
2.956
3.70A
5.122
7.786
2.97A
3.475
A. 835
7.602
8.2A5
3.A42
A.A06
7.251
8.068
9.008
Gas
exhaust
1.166
1.166
1.166
1.166
1.166
1.116
1.116
1.116
1.116
1.116
1.186
1.186
1.186
1.186
1.186
1.256
1.256
1.256
1.256
1.256
1.3A6
1.3A6
1.3A6
1.3A6
1.3A6
1.A36
1.A36
1.A36
1.A36
1.A36
Diesel
exhaust
0.1AA
0.1AA
0.144
0.14A
0.1A4
0.144
0.144
0.144
0.144
0.144
0.144
0.144
0.144
0.144
0.144
0.144
0.144
0.144
0.144
0.144
0.144
0.144
0.144
0.144
0.144
0.144
0.144
0.144
0.1AA
0.144
NOx
3.55
3.55
3.55
3.55
3.55
3.49
3.49
3.49
3.49
3.49
3.32^.
3.32"
3.32
3.32
3.32
3.16
3.16
3.16
3.16
3.16
3.01-
3.01
3.01
3.01
3.01
2.88
2.88
2.88
2.88
2.88
CO
16.42
16.42
16.42
16.42
16.42
15.79
15.79
15.79
15.79
15.79
17.91
17.91
17.91
17.91
17.91
20.51
20.51
20.51
20.51
20.51
23.70
23.70
23.70
23.70
23.70
27.61
27.61
27.61
27.61
27.61
Breakdown of evaporative
emissions
MOBILE 3.9
evajKj"
raL i >>n
1.320
1.390
1.490
1.760
2.170
1.320
1.420
1.620
2.020
2.700
1.320
1.460
1.810
2.480
3.710
1.330
1.5AO
2.170
3.400
5.780
1.330
1.730
2.910
5.390
5.600
1.350
2.160
4.710
5.110
5.300
Running
loss
0.159
0.177
0.211
0.264
0.344
0.242
0.270
0.321
0.402
0.525
0.368
0.412
0.490
0.613
0.800
0.562
0.628
0.746
0.934
1.219
0.856
0.957
1.137
1.424
1.857
1.304
.1 .458
1.734
2.170
2.830
Excess
evapo-
rati on
0.788
0.788
0.788
0.788
0.788
0.788
0.788
0.788
0.788
0.788
0.788
0.788
0.788
0.788
0.788
0.788
0.788
0.788
0.788
0.788
0.788
0.788
0.788
0.788
0.788
0.788
0.788
0.788
0.788
0.788
-------
APPENDIX D. COMPOSITE MOBILE SOURCE EMISSION FACTORS FOR DIFFERENT TEMPERATURES
o
Emissions
Year
1995
1995
1995
1995
1995
1995
1995
1995
1995
1995
1995
1995
1995
1995
1995
1995
1995
1995
1995
1995
1995
1995
1995
1995
1995
1995
1995
1995
1995
1995
Mean
daily
ternp.
(F)
40
40
40
40
4i)
43
45
43
43
45
50
50
50
50
50
55
55
55
55
55
60
60
60
60
60
65
65
65
65
65
(g/mile)
VOC
Range
(F)
0
10
20
30
40
0
10
20
30
40
0
10
20
30
40
0
10
20
30
40
0
10
20
30
40
0
10
20
30
40
Total
1.661
1.661
1.662
1.662
1.663
1.612
1.612
1.613
1.614
1.616
1.544
1.624
1.555.
1.557
1.569
1.506
1.507
1.519
1.531
1.545
1.470
1.472
1.4C4
1.498
1.524
1.436
1.448
1.462
1.488
1.506
Evapo-
rative
0.811
0.811
0.812
0.812
0.813
0.812
0.812
0.813
0.814
0.816
0.804
0.814
0.815
0.817
0.829
0.806
0.807
0.819
0.831
0.845
0.810
0.812
0.824
0.838
0.864
0.816
0.828
0.842
0.868
0.886
Gas
exhaust
0.769
0.769
0.769
0.769
0.769
0.719
0.719
0.719
0.719
0.719
0.659
0.729
0.659
0.659
0.659
0.619
0.619
0.619
0.619
0.619
0.579
0.579
0.579
0.579
0.579
0.539
0.539
0.539
0.539
0.539
Diesel
exhaust
0.081
0.081
0.081
0.081
0.081
0.081
0.081
0.081
0.081
0.081
0.081
0.081
0.081
0.081
0.081
0.081
0.081
0.081
0.081
0.081
0.081
0.081
0.081
0.081
0.081
0.081
0.081
0.081
0.081
0.081
NOx
2.50
2.50
2.50
2.50
2.50
2.44
2.44
2.44
2.44
2.44
2.40
l»
2.47
2.40
2.40
2.40
2.35U
2.35
2.35
2.35
2.35
2.30
2.30
2.30
2.30
2.30
2.26
2.26
2.26
2.26
2.26
CO
10.12
10.12
10.12
10.12
10.12
9.33
9.33
9.33
9.33
9.33
8.60
9.27
8.60
8.60
8.60
7.92
7.92
7.92
7.92
7.92
7.29
7.29
7.29
7.29
7.29
6.70
6.70
6.70
6.70
6.70
Breakdown of evaporative
enii ssions
MOIilLE 3.9
t:vapo- Running
ration loss
0.390
0.390
0.390
0.390
0.390
0.390
0.390
0.390
0.390
0.390
0.380
0.390
0.390
0.390
0.400
0.380
0.380
0.390
0.400
0.410
0.380
0.380
0.390
0.400
0.420
0.380
0.390
0.400
0.420
0.430
0.002
0.002
0.003
0.004
0.005
0.003
0.004
0.004
0.005
0.007
0.005
0.005
0.007
0.008
0.011
0.007
0.008
0.010
0.012
0.016
0.011
0.013
0.015
0.019
0.025
0.017
0.019
0.023
0.029
0.038
Excess
evapo-
rat i on
0.419
0.419
0.419
0.419
0.419
0.419
0.419
0.419
0.419
0.419
0.419
0.419
0.419
0.419
0.419
0.419
0.419
0.419
0.419
0.419
0.419
0.419
0.419
0.419
0.419
0.419
0.419
0.419
0.419
0.419
-------
APPENDIX D. COMPOSITE MOBILE SOURCE EMISSION FACTORS FOR DIFFERENT TEMPERATURES
Emissions
Year
1995
1995
1995
1995
1995
1995
1995
1995
1995
1995
1995
1995
1995
1995
1995
1995
1995
1995
1995
1995
1995
1995
1995
1995
1995
1995
1995
1995
1995
1995
Mean
dai 1>
temp.
(F)
/O
70
70
70
70
75
75
75
75
7:>
8 i)
80
80
80
80
85
85
85
85
85
90
90
9o
90
90
95
95
9'>
95
9:)
(g/mile)
VOC
Range
(F)
0
10
20
30
40
0
10
20
30
40
0
10
20
30
40
0
10
20
30
40
0
10
20
30
40
0
10
20
30
40
Total
1.415
1.428
1.444
1.473
1.546
1.399
1.414
1.452
1.486
1.616
1.440
1 .467
1.500
1 .611
1.802
] .492
1.523
1.583
1.774
2.132
1.571
1.628
1.748
2.086
2.208
1.676
1.742
2.018
2.170
2.350
Evapo-
rative
0.825
0.838
0.854
0.883
0.956
0.839
0.854
0.892
0.926
1.056
0.860
0.887
0.920
1.031
1.222
0.892
0.923
0.983
1.174
1.532
0.941
0.998
1.118
1.456
1.578
1.016
1.082
1.358
1.510
1.690
Gas
exhaust
0.509
0.509
0.509
0.509
0.509
0.479
0.479
0.479
0.479
0.479
0.499
0.499
0.499
0.499
0.499
0.519
0.519
0.519
0.519
0.519
0.549
0.549
0.549
0.549
0.549
0.579
0.579
0.579
0.579
0.579
Diesel
exhaust
0.081
0.081
0.081
0.081
0.081
0.081
0.081
0.081
0.081
0.081
0.081
0.081
0.081
0.081
0.081
0.081
0.081
0.081
0.081
0.081
0.081
0.081
0.081
0.081
0.081
0.081
0.081
0.081
0.081
0.081
NOx
2.21
2.21
2.21
2.21
2.21
2.17
2.17
2.17
2.17
2.17
1.96
1.96""
1.96
1.96
1.96
1.78
1.78
• 1.78
1.78
1.78
1.62
1.62
1.62
1.62
1.62
1.49
1.49
1.49
1.49
1.49
CO
6.14
6.14
6.14
6.14
6.14
5.62
5.62
5.62
5.62
5.62
6.08
6.08
6.08
6.08
6.08
6.63
6.63
6.63
6.63
6.63
7.29
7.29
7.29
7.29
7.29
8.10
8.10
8.10
8.10
8.10
Breakdov/n of • evaporative
emissions
MOBILE 3.9
evapo- Running
ration loss
0.380
0.390
0.400
0.420
0.480
0.380
0.390
0.420
0.440
0.550
0.380
0.400
0.420
0.510
0.670
0.380
0.400
0.440
0.600
0.910
0.380
0.420
0.510
0.800
0.850
0.380
0.420
0.650
0.730
0.800
0.026
0.030
0.035
0.044
0.057
0.040
0.045
0.054
0.067
0.087
0.061
0.069
0.082
0.102
0.133
0.094
0.105
0.124
0.156
' 0.203
0.143
0.159
0.190
0.237
0.309
0.217
0.243
0.289
0.362
0.472
Excess
evapo-
rat ion
0.419
0.419
0.419
0.419
0.419
0.419
0.419
0.419
0.419
0.419
0.419
0.419
0.419
0.419
0.419
0.419
0.419
0.419
0.419
0.419
0.419
0.419
0.419
0.419
0.419
0.419
0.419
0.419
0.419
0.419
-------
APPENDIX D. COMPOSITE MOBILE SOURCE EMISSION FACTORS FOR DIFFERENT TEMPERATURES
a
Emissions
Year
2005
2005
2005
2005
2005
2005
2005
2005
2005
2005
2005
2005
2005
2005
2005
2005
2005
2005
2005
2005
2005
2005
2005
2005
2005
2005
2005
2005
2005
2005
Me.m
dai ly
temp.
(F)
40
40
40
40
40
45
45
45
45
45
50
50
50
50
50
55
55
55
55
55
60
60
60
60
60
65
65
65
65
65
VOC
Range
(F)
0
10
20
30
40
0
10
20
30
40
0
10
20
30
40
0
10
20
30
40
0
10
20
30
40
0
10
20
30
40
Total
1.451
1.452
1.452
1.453
1.454
1.402
1.403
1.403
1.405
1.416
1.344
1.415
1.356
1.367
1.370
1.307
1.308
1.319
1.332
1.345
1.281
1.292
1.304
1.308
1.334
1.246
1.259
1.272
1.288
1.307
Evapo-
rative
0.731
0.732
0.732
0.733
0.734
0.732
0.733
0.733
0.735
0.746
0.724
0.735
0.736
0.747
0.750
0.727
0.728
0.739
0.752
0.765
0.731
0.742
0.754
0.758
0.784
0.736
0.749
0.762
0.778
0.797
Gas
exhaust
0.645
0.645
0.645
0.645
0.645
0.595
0.595
0.595
0.595
0.595
0.545
0.605
0.545
0.545
0.545
0.505
0.505
0.505
0.505
0.505
0.475
0.475
0.475
0.475
0.475
0.435
0.435
0.435
0.435
0.435
(g/mile)
Diesel
exhaust
0.075
0.075
0.075
0.075
0.075
0.075
0.075
0.075
0.075
0.075
0.075
0.075
0.075
0.075
0.075
0.075
0.075
0.075
0.075
0.075
0.075
0.075
0.075
0.075
0.075
0.075
0.075
0.075
0.075
0.075
NOx
2.29
2.29
2.29
2.29
2.29
2.24
2.24
2.24
2.24
2.24
2.20
2.26"
,2.20
2.20
2.20
2.15
2.15
2.15
2.15
2.15
2.11
2.11
2.11
2.11
2.11
2.07
2.07
2.07
2.07
2.07
CO
8.79
8.79
8.79
8.79
8.79
8.04
8.04
8.04
8.04
8.04
7.34
7.97
7.34
7.34
7.34
6.69
6.69
6.69
6.69
6.69
6.09
6.09
6.09
6.09
6.09
5.52
5.52
5.52
5.52
5.52
Breakdown ol' evaporative
emi ssions
MOBILE 3.9
evapo- Running
ration loss
0.310
0.310
0.310
0.310
0.310
0.310
0.310
0.310
0.310
0.320
0.300
0.310
0.310
0.320
0.320
0.300
0.300
0.310
0.320
0.330
0.300
0.310
0.320
0.320
0.340
0.300
0.310
0.320
0.330
0.340
0.002
0.002
0.003
0.004
0.005
0.003
0.004
0.004
0.005
0.007
0.005
0.005
0.007
0.008
• 0.011
0.007
0.008
0.010
0.012
0.016
0.011
0.013
0.015
0.019
0.025
0.017
0.019
0.023
0.029
0.038
Excess
evapo-
ration
0.419
0.419
0.419
0.419
0 . 4 1
-------
APPENDIX D. COMPOSITE MOBILE SOURCE EMISSION FACTORS FOR DIFFERENT TEMPERATURES
o
Emissions
Year
2005
2005
2005
2005
2005
2005
2005
2005
2005
2005
2005
2005
2005
2005
2005
2005
2005
2005
2005
2005
2005
2005
2C05
2005
2005
2005
2005
2005
2005
2005
Mean
dai ly
tern p.
00
70
70
VO
70
70
75
75
75
75
7:i
fcu
80
80
8u
80
6:>
8i
8:>
8'j
85
90
90
90
90
90
95
9'J
9l>
9:>
95
(g/mile)
VOC
Range
(F)
0
10
20
30
40
0
10
20
30
40
0
10
20
30
40
0
10
20
30
40
0
10
20
30
40
0
10
20
30
40
Total
1.236
1.249
1.264
1.293
1.347
1.219
1.244
1.263
1.296
1.407
1.251
1.278
1.311
1.391
1.582
1.283
1.314
1.374
1.545
1.872
1.342
1.389
1.499
1.816
1.949
1.426
1.492
1.738
1.881
2.061
Evapo-
rative
0.746
0.759
0.774
0.803
0.857
0.759
0.784
0.803
0.836
0.947
0.781
0.808
0.841
0.921
1.112
0.813
0.844
0.904
1.075
1.402
0.862
0.909
1.019
1.336
1.469
0.936
1.002
1.248
1.391
1.571
Gas
exhaust
0.415
0.415
0.415
0.415
0.415
0.385
0.385
0.385
0.385
0.385
0.395
0.395
0.395
0.395
0.395
0.395
0.395
0.395
0.395
0.395
0.405
0.405
0.405
0.405
0.405
0.415
0.415
0.415
0.415
0.415
Diesel
exhaust
0.075
0.075
0.075
0.075
0.075
0.075
0.075
0.075
0.075
0.075
0.075
0.075
0.075
0.075
0.075
0.075
0.075
0.075
0.075
0.075
0.075
0.075
0.075
0.075
0.075
0.075
0.075
0.075
0.075
0.075
NOx
2.03
2.03
2.03
2.03
2.03
1.99
1.99
1.99
1.99
1.99
1.77^
1.77"
1.77
1.77
1.77
1.59
1.59
1.59
1.59
1.59
1.44
1.44
1.44
1.44
1.44
1.31
1.31
1.31
1.31
1.31
CO
5.00
5.00
5.00
5.00
5.00
4.50
4.50
4.50
4.50
4.50
4.69
4.69
4.69
4.69
4.69
4.89
4.89
4.89
4.89
4.89
5.12
5.12
5.12
5.12
5.12
5.37
5. 37
5.37
5.37
5.37
Breakdown of evaporative
emissions
MOBILE 3.9
evapo- Running
ration loss
0.300
0.310
0.320
0.340
0.380
0.300
0.320
0.330
0.350
0.440
0.300
0.320
O'. 340
0.400
0.560
0.300
0.320
0.360
0.500
0.7 MO
0.300
0.330
0.410
0.680
0.740
0.300
0.340
0.540
0.610
0.680
0.026
0.030
U.035
(J.044
0.057
0.040
0.045
0.054
0,067
0.087
n.061
0.069
0.082
0.102
0.133
0.094
0.105
0.124
0.156
ij.203
U.J43
0.159
0.190
0.237
0.309
0.217
0.243
0.289
0.362
0.472
Excess
evapo-
rat ion
0.419
0.419
0.419
0.419
0.419
0.419
0.419
0.419
0.419
0.419
0.419
0.419
0.419
0.41 9
0.419
0.419
0.419
0.419
0.419
0.419
0.419
0.419
0.419
0.419
0.419
0.419
0.419
0.419
0.419
0.419
-------
TECHNICAL REPORT DATA
'Please read Instructions on the reverse before completing)
1. REPORT NO.
3. RECIPIENT'S ACCESSiOf^ NO.
4. TITLE AND SUBTITLE
Regional Ozone Modeling for Northeast Transport
Development of a Base Year Anthropogenic
Emissions Inventory
5. REPORT DATE
May 1989
5. PERFORMING ORGANIZATION CODE
7. AUTHOR(S)
William Battye, John Langstaff, Mark Smith, Jan Demmy,
Teresa Richardson, Teresa Lynch, Roger Cawkwell
8. PERFORMING ORGANIZATION REPORT NO.
EPA-450/4-89-008
9. PERFORMING ORGANIZATION NAME AND ADDRESS
Alliance Technologies Corporation
100 Europa Drive
Chapel Hill, NC 27514
10. PROGRAM ELEMENT NO.
11. CONTRACT/GRANT NO.
68-02-4396
12. SPONSORING AGENCY NAME AND ADDRESS
U. S. Environmental Protection Agency
Office of Air Quality Planning and Standards
Research Triangle Park, NC 27711
13. TYPE OF REPORT AND PERIOD COVERED
Final
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15. SUPPLEMENTARY NOTES
EPA Project Officer: Edwin L. Meyer, Jr.
16. ABSTRACT
Pollutant transport is especially pronounced in the Northeastern United States, where
several urban areas are in close proximity to one another. In order to quantify the
concentrations of pollutants transported among urban areas and to identify and assess
strategies for attaining the ozone NAAQS in the Northeast, the U. S. Environmental
Protection Agency is undertaking a program of Regional Ozone Modeling for Northeast
Transport (ROMNET). This report describes the preparation of the ROMNET base year
(1985) emission inventory. Pollutants covered include volatile organic compounds (VOC)
oxides of nitrogen (NQX) and carbon monoxide (CO).
17.
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Ozone
VOC control strategies
NOX control strategies
emission inventories
regional modeling
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