&EPA
United States
Environmental Protection
Agency
Region II Office
26 Federal Plaza
New York, N.Y. 10007
EPA 902/4-79-001
March 1979
Air
New Jersey Area Source
VOC and NOx Emissions
Inventory
For Selected Counties and
Categories
-------
SUMMARY REPORT
NEW JERSEY AREA SOURCE VOC AND NO
X
EMISSIONS INVENTORY
(FOR SELECTED COUNTIES AND CATEGORIES)
Submitted to
Environmental Protection Agency
Air Programs Branch
Environmental Programs Division
Region II
6 Federal Plaza
New York, New York 10007
Contract No. 68-02-2537 Task Order No. 5
EPA Project Officer: Paul R. Truchan
Submitted by
Engineering-Science
7903 Westpark Drive
McLean, Virginia 22102
March 1979
-------
This air pollution report is issued by Region II
Environmental Protection Agency to assist state and
local air pollution control agencies in carrying out
their program activities. Copies of this report may
be obtained for a nominal cost, from the National
Technical Information Service, 5285 Port Royal Road,
Springfield, Virginia 22151.
This report was furnished to the Environmental Pro-
tection Agency by Engineering-Science, Inc., McLean,
Virginia in fulfillment of EPA Contract No. 68-02-2537.
This report has been reviewed by Region II, EPA and
approved for publication. Approval does not signify
that the contents necessarily reflect the views and
policies of the Environmental Protection Agency,
nor does mention of trade names or commercial products
constitute endorsement or recommendation for use.
Region II Publication No. 902/4-79-001
-------
TABLE OF CONTENTS
CHAPTER I
CHAPTER II
CHAPTER III
CHAPTER IV
CHAPTER V
CHAPTER VI
CHAPTER VII
CHAPTER VIII
INTRODUCTION
BACKGROUND
METHODS
REPORT ORGANIZATION
POPULATION, EMPLOYMENT, AND GROWTH FACTORS
POPULATION
EMPLOYMENT
GROWTH FACTORS
ASPHALT PAVING
BASE YEAR
PROJECTION YEARS
OXIDANT SEASON
PESTICIDES
BASE YEAR
PROJECTION YEARS
OXIDANT SEASON
FOREST FIRES
BASE YEAR
PROJECTION YEARS
OXIDANT SEASON
AGRICULTURAL BURNING
BASE YEAR
PROJECTION YEARS
OXIDANT SEASON
STRUCTURAL FIRES
BASE YEAR
PROJECTION YEARS
OXIDANT SEASON
NATURAL SOURCE EMISSIONS
BASE YEAR
PROJECTION YEARS
OXIDANT SEASON
Page
1-1
1-1
1-1
1-2
II-l
II-l
II-2
II-3
III-l
III-l
III-l
III-l
IV-1
IV-1
IV-1
IV-1
V-l
V-l
V-l
V-l
VI-1
VI-1
VI-1
VI-2
VII-1
VII-1
VII-1
VII-1
VIII-1
VIII-1
VIII-2
VIII-2
-------
TABLE OF CONTENTS (CONTINUED)
CHAPTER IX
CHAPTER X
CHAPTER XI
CHAPTER XII
CHAPTER XIII
CHAPTER XIV
CHAPTER XV
CHAPTER XVI
SURFACE COATINGS
BASE YEAR
PROJECTION YEARS
OXIDANT SEASON
INCINERATORS
BASE YEAR
PROJECTION YEARS
OXIDANT SEASON
OPEN BURNING
BASE YEAR
PROJECTION YEARS
OXIDANT SEASON
RAILROADS
BASE YEAR
PROJECTION YEARS
OXIDANT SEASON
AIRCRAFT
BASE YEAR
PROJECTION YEARS
OXIDANT SEASON
VESSELS
BASE YEAR
PROJECTION YEARS
OXIDANT SEASON
OFF-HIGHWAY VEHICLES
GENERAL UTILITY ENGINES
FARM TRACTORS
CONSTRUCTION EQUIPMENT
RESIDENTIAL HEATING FUEL
BASE YEAR
PROJECTION YEARS
OXIDANT SEASON
Page
IX-1
IX-1
IX-1
IX-1
X-l
X-l
X-2
X-2
XI-1
XI-1
XI-1
XI-3
XII-1
XII-1
XII-1
XII-3
XIII-1
XIII-1
XIII-1
XIII-4
XIV-1
XIV-1
XIV-4
XIV-4
XV-1
XV-1
XV-5
XV-7
XVI-1
XVI-1
XVI-1
XVI-4
ii
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TABLE OF CONTENTS (CONTINUED)
Page
CHAPTER XVII
CHAPTER XVIII
CHAPTER XIX
CHAPTER XX
APPENDIX A
APPENDIX B
COMMERCIAL FUEL
BASE YEAR
PROJECTION YEARS
OXIDANT SEASON
LIGHT INDUSTRIAL FUEL
BASE YEAR
PROJECTION YEARS
OXIDANT SEASON
SLASH BURNING
COUNTY AND AQCR EMISSION SUMMARIES
NEDS FORMATED DATA
COUNTY ACTIVITY PARAMETERS
XVII-1
XVII-1
XVII-1
XVII-3
XVIII-1
XVIII-1
XVIII-1
XVIII-3
XIX-1
XX-1
LIST OF TABLES
TABLE
TABLE
TABLE
TABLE
TABLE
TABLE
TABLE
TABLE
TABLE
TABLE
TABLE
TABLE
II-l
II-2
II-3
II-4
III-l
III-2
IV-1
IV-2
V-l
V-2
VI-1
VI-2
TABLE VII-1
TABLE VII-2
POPULATION DATA II-3
CONSTRUCTION EMPLOYMENT II-5
WHOLESALE AND RETAIL EMPLOYMENT II-6
MANUFACTURING EMPLOYMENT II-7
ESTIMATES ASPHALT PAVING EMISSIONS III-2
ESTIMATES ASPHALT PAVING OXIDANT SEASON EMISSIONS III-3
ESTIMATED PESTICIDE EMISSIONS IV-2
ESTIMATED PESTICIDE OXIDANT SEASON EMISSIONS IV-3
ESTIMATED FOREST FIRE EMISSIONS V-2
ESTIMATED FOREST FIRE OXIDANT SEASON EMISSIONS V-3
ESTIMATED AGRICULTURAL BURNING EMISSIONS VI-3
ESTIMATED AGRICULTURAL BURNING OXIDANT SEASON
EMISSIONS VI-4
ESTIMATED STRUCTURAL FIRE EMISSIONS VII-2
ESTIMATED STRUCTURAL FIRE OXIDANT SEASON
EMISSIONS VII-3
iii
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TABLE OF CONTENTS (CONTINUED)
LIST OF TABLES.(CONTINUED)
Page
TABLE VIII-1
TABLE VIII-2
TABLE IX-1
TABLE IX-2
TABLE
TABLE
TABLE
TABLE
TABLE
TABLE
TABLE
TABLE
TABLE
TABLE
TABLE
TABLE
TABLE
TABLE
TABLE
TABLE
TABLE
TABLE
TABLE
TABLE
TABLE
X-l
X-2
XI-1
XI-2
XII-1
XI I-2
XIII-1
XIII-2
XIII-3
XIV-1
XIV-2
XIV-3
XIV-4
XV-1
XV-2
XV-3
XV-4
XV-5
XVI-1
XVI-2
XVI-3
ESTIMATED NATURAL SOURCE EMISSIONS VIII-3
ESTIMATED NATURAL SOURCE OXIDANT SEASON
EMISSIONS VIII-4
ESTIMATED SURFACE COATING EMISSIONS IX-2
ESTIMATED SURFACE COATING OXIDANT SEASON
EMISSIONS IX-3
ESTIMATED INCINERATOR EMISSIONS X-3
ESTIMATED INCINERATOR OXIDANT SEASON EMISSIONS X-4
ESTIMATED OPEN BURNING EMISSIONS XI-2
ESTIMATED OPEN BURNING OXIDANT SEASON EMISSIONS XI-4
ESTIMATED RAILROAD EMISSIONS XII-2
ESTIMATED RAILROAD OXIDANT SEASON EMISSIONS XII-4
AIRCRAFT EMISSION FACTORS XIII-2
ESTIMATED AIRCRAFT EMISSIONS XIII-3
ESTIMATED AIRCRAFT OXIDANT SEASON EMISSIONS XIII-5
ESTIMATED VESSEL EMISSIONS XIV-2
EMISSIONS FROM CARGO VESSELS XIV-3
EMISSIONS FROM PLEASURE, CHARTER, AND LIVERY
BOATS BY COUNTY XIV-5
ESTIMATED VESSEL OXIDANT SEASON EMISSIONS XIV-6
ESTIMATED OFF-HIGHWAY VEHICLE EMISSIONS XV-2
ESTIMATED OFF-HIGHWAY OXIDANT SEASON EMISSIONS XV-3
ESTIMATED GENERAL UTILITY ENGINE EMISSIONS XV-4
ESTIMATED FARM TRACTOR EMISSIONS XV-6
ESTIMATED DIESEL CONSTRUCTION EQUIPMENT EMISSIONS XV-8
ESTIMATED RESIDENTIAL HEATING FUEL EMISSIONS XVI-2
RESIDENTIAL HEATING FUEL EMISSION FACTORS XVI-3
ESTIMATED RESIDENTIAL HEATING FUEL OXIDANT
SEASON EMISSIONS XVI-5
iv
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TABLE OF CONTENTS (CONTINUED)
LIST OF TABLES (CONTINUED)
Page
TABLE XVII-1
TABLE XVII-2
TABLE XVIII-1
TABLE XVIII-2
TABLE XX-1
TABLE XX-2
TABLE XX-3
TABLE XX-4
TABLE XX-5
ESTIMATED COMMERCIAL FUEL EMISSIONS
ESTIMATED COMMERCIAL FUEL OXIDANT SEASON
EMISSIONS
ESTIMATED LIGHT INDUSTRIAL FUEL EMISSIONS
ESTIMATED LIGHT INDUSTRIAL FUEL OXIDANT
SEASON EMISSIONS
ESTIMATED TOTAL EMISSIONS
ESTIMATED TOTAL OXIDANT SEASON EMISSIONS
ESTIMATED TOTAL EMISSIONS
ESTIMATED TOTAL OXIDANT SEASON EMISSIONS
AIR QUALITY CONTROL REGIONS
XVII-2
XVII-4
XVIII-2
XVIII-4
XX-2
XX-3
XX-4
XX-5
XX-6
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CHAPTER I
INTRODUCTION
BACKGROUND
Engineering-Science (ES) was contracted by the U. S. Environmental Pro-
tection Agency to assist the New Jersey Department of Environmental Protection
(NJDEP) in the development of area source emission data for certain categories
and counties not previously evaluated. Both volatile organic compounds and
oxides of nitrogen emissions were determined. The purpose of the effort was
to provide NJDEP with the basic data necessary for their State Implementation
revision mandated by the Clean Air Act as amended in 1977.
Ten categories were examined state-wide, two other categories were evalu-
ated for 16 of the 21 New Jersey counties, and an additional seven categories
were addressed for seven counties. The base year of the study was 1975 and
projections were made for 1977, 1982, and 1987.
The annual emission estimates were adjusted to reflect the quantity of
emissions which occurred during the oxidant season versus the remainder of the
year. The NJDEP defined the New Jersey oxidant season as beginning on April 1
and extending through September 30.
Emissions were summarized by county and air quality control region as shown
in Chapter XX. The raw data from which the emissions were calculated are shown
in NEDS format in Appendix A.
METHODS
In general, EPA methods for calculating and projecting emissions were used.
The procedures utilized by ES were reviewed and approved by EPA and NJDEP before
and during the study. The EPA publications used for this study include the
following:
Procedures for the Preparation of Emission Inventories for Volatile Organic
Compounds, Volume 1, EPA 450/2-77-028, December, 1977.
Guidelines for Air Quality Maintenance Planning and Analysis, Volume 7:
Projecting County Emissions, Second Edition, EPA 450/4-74-008, January
1975.
Compilation of Air Pollution Emission Factors, AP-42 (with supplement 8).
1-1
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Regional Air Pollution Study Off-Highway Mobile Source Emission Inventory,
EPA 600/4-77/041, October 1977.
REPORT ORGANIZATION
Chapter II deals with the population, employment, and historical growth
factors utilized in this study. The origin of all three considerations are
reviewed in detail.
Chapters III through XIX relate the methods, assumptions, emission factors,
and projection factors used in determining emissions for each category addressed
in the study. The annual and oxidant season emissions are presented by county
for each category.
Chapter XX summarizes the total emissions from Chapters III through XIX.
Emissions are presented by county and air quality control region for both annual
and oxidant season emissions.
Appendices A and B summarize the county activity parameters in two different
ways. Appendix A is in the NEDS format, while Appendix B summarizes the actual
data referenced in the study by category and county.
1-2
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CHAPTER II
POPULATION, EMPLOYMENT. AND GROWTH FACTORS
POPULATION
County population estimates for 1975 were obtained from three sources* The
N.J. State Department of Labor & Industry, Division of Planning & Research, Office
of Demographic & Economic Analysis supplied population estimates for 1975 and
population projection data for 1980, 1985, and 1990. This population data can
be found in their New Jersey Interim Population Projections 1980-2000, "Demo-
graphic-Economic Linked Model". The interpolated ODEA population information
was applied in the following counties:
Atlantic
Cape May
Cumberland
Hunterdon
Ocean
Salem
Sussex
Warren
The Delaware Valley Regional Planning Commission published 1970 and 2000
population estimates in their Year 2000 Report Number Five Policy Statement on
Regional Development. ES requested that DVRPC assist in determining population
values for the years of interest, 1975, 1977, 1982 and 1987. DVRPC's suggested
method was to utilize the annual increments provided in their September 1977,
Interim Projections Report. The resulting population estimates were used in the
following counties:
Burlington
Camden
Gloucester
Mercer
The Tri-State Regional Planning Commission supplied 1970 and 2000 popula-
tion estimates in their Regional Development Guide, 1977-2000. This population
information also needed to be related to the years of interest. As recommended
by the NJDEP, ES adopted the same approach as the Delaware Valley Regional
Planning Commission had suggested. The annual increments used for the Tri-
II-l
-------
State population data were obtained from the New Jersey Department of Environ-
ment Protection, Division of Water Resources's New Jersey Water Supply Master
Plan. These population estimates were used in the following counties:
Bergen
Essex
Hudson
Middlesex
Monmouth
Morris
Passaic
Somerset
Union
Population estimates and projection factors used in this study are
listed in Table II-l. This table represents the resulting population infor-
mation from the three sources of data.
EMPLOYMENT
Employment estimates came from two sources. The New Jersey Department of En-
vironment Protection, Division of Water Resources, supplied 1975, 1980, 1982 and
1987 employment data for construction, manufacturing, and wholesale-retail em-
ployees in their New Jersey Water Supply Master Plan. Employment values for
1977 were calculated by linear interpolation between the 1975 and 1980 data
for each of the three employment categories. These employment estimates were
used for the following counties:
Atlantic
Bergen
Cape May
Cumberland
Essex
Hudson
Hunterdon
Middlesex
Monmouth
Morris
II-2
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TABLE II-l
POPULATION DATA
Atlantic
Bergen
Burlington
Camden
Cape May
Cumberland
Essex
Gloucester
Hudson
Hunter don
Mercer
Middlesex
Monmouth
Morris
Ocean
Passaic
Salem
Somerset
Sussex
Union
Warren
1975
ESTIMATE
187,900
918,333
344,506
481,970
72,300
132,000
938,333
190,458
609,166
78,500
319,921
623,333
485,833
406,666
293,800
474,167
62,400
211,667
99,000
550,833
80,000
1977
1.046
1.009
1.093
1.079
1.077
1.021
1.004
1.146
1.000
1.028
1.074
1.025
1.022
1.022
1.091
1.011
1.002
1.026
1.073
1.006
1.025
POPULATION GROWTH FACTORS
1982
1.256
1.031
1.152
1.130
1.351
1.084
1.012
1.236
1.000
1.095
1.120
1.088
1.077
1.078
1.316
1.039
1.011
1.090
1.244
1.020
1.074
1987
1.534
1.053
1.172
1.172
1.700
1.162
1.021
1.307
1.001
1.166
1.157
1.151
1.133
1.134
1.527
1.067
1.038
1.155
1.411
1.034
1.124
II-3
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Ocean
Passaic
Salem
Somerset
Sussex
Union
Warren
The Delaware Valley Regional Planning Commission supplied employment
estimates for the other four counties from their Year 2000 Report Number
Five Policy Statement on Regional Development for the years 1970 and 2000.
The DVRPC again suggested calculating the employment estimates for the years
of interest by the annual increment method using their 1977 Interim Projec-
tions Report. The employment estimates from DVRPC were used for: Burlington,
Camden, Gloucester, and Mercer Counties.
The employment estimates and projection .factors used.in this study are
listed in Tables II-2, II-3, and II-4. The categories include construction,
wholesale and retail, and manufacturing employment.
GROWTH FACTORS
Whenever possible documented projection information was utilized to
project future emissions from base year estimates. However, from time to time
it became necessary to seek alternate methods of projecting future emissions.
One such method used was the adoption of historical trends; that is, develop-
ing a model to explain the historical variation. By adopting such a method
it was possible to find an historical trend which fit the most probable pro-
jecting pattern better than any established projection factors. For example,
the historical change in orchard acres was a better projection factor for the
open burning of orchard prunings than the number of farm employees. This
method of projecting emissions was used whenever historical data was identi- -
fied as the projection method.
Promulgated regulations and expected source changes were taken into con-
sideration when projecting emissions. For example, the nitrogen oxide regula-
tions which will affect commercial aircraft emissions by the late 1980's were
taken into account in determining 1987 emissions.
II-4
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TABLE II-2
CONSTRUCTION EMPLOYMENT
Atlantic
Cape May
Cumberland
Hunter don
Ocean
Sussex
Warren
1975
ESTIMATE
4,240
2,462
2,405
1,532
5,715
1,367
1,431
1977
.994
1.057
1.058
.988
1.058
1.085
1.070
GROWTH FACTORS
1982
.942
1.162
1.156
.978
1.170
1.221
1.182
1987
.831
1.208
1.183
.997
1.233
1.239
1.203
II-5
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TABLE II-3
Atlantic
Bergen
Burlington
Camden
Cape May
Cumberland
Essex
Gloucester
Hudson
Hunter don
Mercer
Middlesex
Monmouth
Morris
Ocean
Passaic
Salem
Somerset
Sussex
Union
Warren
WHOLESALE AND
1975
ESTIMATE
16,964
102,989
23,504
42^249
4,965
8,326
75,152
10,769
44,793
5,299
27,012
54,041
35,157
26,923
16,563
42,348
3,024
16,370
4,475
57,624
5,358
RETAIL
1977
1.019
1.082
1.034
1.025
1.007
1.047
1.031
1.060
1.040
1.044
1.031
1.054
1.038
1.047
1.079
1.047
1.050
1.078
1.088
1.069
1.045
EMPLOYMENT
GROWTH FACTORS
1982
1.061
1.244
1.109
1.083
1.049
1.131
1.044
1.191
1.092
1.158
1.098
1.187
1.133
1.156
1.260
1.135
1.130
1.245
1.268
1.182
1.143
1987
1.092
1.344
1.172
1.130
1.131
1.167
.960
1.293
1.073
1.276
1.152
1.317
1.229
1.251
1.418
1.177
1.142
1.368
1.389
1.204
1.217
II-6
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TABLE II-4
MANUFACTURING EMPLOYMENT
Atlantic
Bergen
Burlington
Camden
Cape May
Cumberland
Essex
Gloucester
Hudson
Hunter don
Mercer
Middlesex
Monmouth
Morris
Ocean
Passaic
Salem
Somerset
Sussex
Union
Warren
1975
ESTIMATE
8,428
102,912
23,838
47,395
1,231
17,727
90,879
13,908
77,881
4,778
44,074
84,464
20,889
40,285
4,918
62,434
11,480
26,039
2,837
80,089
13,483
1977
1.042
1.007
1.024
1.004
.949
1.033
.991
1.057
1.008
.996
1.016
.994
1.041
1.013
1.040
1.020
.966
.954
.966
1.029
.992
GROWTH FACTORS
1982
1.112
1.029
1.078
1.012
.980
1.079
.953
1.043
.991
.991
1.050
.997
1.102
1.056
1.129
1.033
.921
.911
.924
1.062
1.003
1987
1.129
1.058
1.124
1.019
.864
1.068
.891
1.065
.919
.992
1.078
1.030
1.103
1.114
1.198
.987
.932
.975
.944
1.034
1.061
II-7
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CHAPTER III
ASPHALT PAVING
Asphalt paving emissions consist of the volatile organic compounds which
evaporate into the ambient air during road paving operations. The cutback
asphalt and emulsified asphalt used as a sealer before paving are the source
of the volatile organic compounds estimated in this chapter.
BASE YEAR
The "Mineral Industry Surveys" for 1975 and 1977 contained state totals
for the consumption of cutback and emulsified asphalts. Apportionment to
counties was based on the number of total road miles within each county as
provided by the New Jersey Department of Transportation. Data from Exxon
suggests that 73% of the cutback used in New Jersey is rapid cure, while 27%
of the cutback is medium cure. Based on information in EPA 450/2-77-028 and
a Virginia Air Pollution Control Board - U. S. E. P. A. Agreement, it was
assumed that 70% by weight of the medium cure, 80% by weight of the rapid cure,
and 6.3% by weight of the emulsified evaporated. The total emissions estimated
for asphalt paving are listed in Table III-l.
PROJECTION YEARS
The 1982 and 1987 emissions were projected from 1975 based on expected
population change. The projected emissions for cutback asphalt will be
reduced by a New Jersey regulation that will restrict future cutback asphalt
usage.
OXIDANT SEASON
Oxidant season emissions were developed with the cooperation of the New
Jersey Department of Transportation, which resulted in an estimate that 66.7%
of the annual emissions occurred in the oxidant season. Table III-2 contains
the oxidant season asphalt paving emissions.
III-l
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TABLE III-I
ESTIMATED ASPHALT PAVING EMISSIONS
(TPY)
Atlantic
Bergen
Burlington
Camden
Cape May
Cumberland
Essex
Gloucester
Hudson
Hunterdon
Mercer
Middlesex
Monmouth
Morris -
Ocean
Passaic
Salem
Somerset
Sussex
Union
Warren
1975
VOC
1412.
2010
1532
1292
670
886
1157
957
430
838
886
1484
1891
1603
1724
886
622
909
934
1029
718
1977
VOC
.,1543
2198
1674
1413
732
968
1308
1046
470
915
968
1622
2067
1752
1884
968
680
994
1020
1125
784
1982
VOC
1773
2072
1764
1460
905
960
1171
1182
430
917
992
1614
2036
1728
2268
920
628
990
1143
1049
771
1987
VOC
2.106
2116
1841
1514
1139
1029
1181
1250
430
977
1025
1708
2142
1817
2632
945
645
1049
1317
1063
807
State Total 23870 26131 26773 28733
III-2
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TABLE III-2
Atlantic
Bergen
Burlington
Camden
Cape May
Cumberland
Essex
Gloucester
Hudson
Hunterdon
Mercer
Middlesex
Monmouth
Morris
Ocean
Passaic
Salem
Somerset
Sussex
Union
Warren
ESTIMATED ASPHALT
1975
VOC
942
1,341
1,022
862
447
591
772
638
287
559
591
990
1,261
1,069
1,150
691
415
606
623
686
479
PAVING OXIDANT
(TPS)
1977
VOC
1,029
1,466
1,117
942
488
646
872
698
313
610
646
1,081
1,379
1,169
1,257
646
454
663
680
750
523
SEASON EMISSIONS
1982
VOC
1,183
1,382
1,177
974
604
640
781
788
287
612
662 '
1,077
1,358
1,153
1,513
614
419
660
762
700
514
1987
VOC
1,445
1,411
1,228
1,010
760
686
788
834
287
652
684
1,139
1,429
1,212
1,756
630
430
700
878
709
538
State Total
16,022
17,429
17,860
19,206
III-3
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CHAPTER IV
PESTICIDES
Pesticide emissions consist of the volatile organic compounds which
evaporate into the ambient air from the insecticides, herbicides, fungicides,
fumigants, and acaricides used by man. This estimate of emissions does not
include the use of pesticides by the homeowner.
BASE YEAR
Pesticide information was obtained from a 1976 New Jersey Department of
Health study titled "New Jersey Epidemologic Studies Program - Report on
Pesticide Usage Study". The New Jersey DOH report provides the total pounds
of active ingredients from agricultural and nonagricultural pesticides used in
each county. Because of the variety of pesticides included in the activity
parameter, no estimation of the total inert content could be established;
therefore, no emissions could be calculated for the inert ingredients. Assum-
ing that 90% of the active ingredients volatize as suggested by EPA 450/2-
77-028, the emissions were estimated as listed in Table IV-1.
PROJECTION YEARS
All emissions were projected from the 1976 data assuming a 1% annual
increase, as agreed upon with the New Jersey DOH.
OXIDANT SEASON
Assuming pesticides are used during the same season as farm equipment,
74.6% of the annual emissions occurred in the oxidant season. Table IV-2
contains the oxidant season emissions for pesticides.
IV-1
-------
TABLE IV-1
Atlantic
Bergen
Burlington
Camden
Cape May
Cumberland
Essex
Gloucester
Hudson
Hunterdon
Mercer
Middlesex
Monmouth
Morris
Ocean
Passaic
Salem
Somerset
Sussex
Union
Warren
ESTIMATED
1975
VOC
158
65
251
106
17
156
54
390
31
81
74
98
179
56
36
26
128
53
63
35
79
PESTICIDE EMISSIONS
(TPY)
1977
VOC
162
67
257
108
17
160
56
398
31
83
76
100
183
58
36
26
130
55
65
35
81
1982
VOC
170
70
270
114
18
168
58
418
33
87
80
105
192
61
38
28
137
57
68
37
85
1987
VOC
179
74
283
119
19
176
61
440
35
91
84
110
202
64
40
29
144
60
71
39
89
State Total
2136
2184
2294
2409
IV-2
-------
TABLE IV-2
Atlantic
Bergen
Burlington
Camden
Cape May
Cumberland
Essex
Gloucester
Hudson
Hunterdon
Mercer
Middlesex
Monmouth
Morris
Ocean
Passaic
Salem
Somerset
Sussex
Union
Warren
ESTIMATED PESTICIDE
1975
VOC
118
49
188
79
13
117
41
291
23
61
55
73
134
42
27
19
95
40
47
26
59
OXIDANT SEASON
(TPS)
1977
VOC
121
50
191
81
13
119
41
297
23
62
57
75
136
43
27
20
97
41
48
26
60
EMISSIONS
1982
VOC
127
52
201
85
13
125
44
312
25
65
59
78
143
45
29
21
102
43
51
28
63
1987
VOC
134
55
211
89
14
132
46
328
26
68
62
82
151
47
30
22
107
45
53
29
67
State Total 1597 1628 1711 1798
IV-3
-------
CHAPTER V
FOREST FIRES
The quantity of volatile organic compounds and oxides of nitrogen given
off as emissions during a forest fire depends upon the quantity of material
burned. Wild forest fires are the only source of emissions included in this
category.
BASE YEAR
The forest fire emission calculations were based on the quantity of
material burned in 1975 by county as supplied by the New Jersey State Fire-
warden's Office and the following emission factors from AP-42:
VOC 23.67 Ibs/ton of material burned
NO 3.92 Ibs/ton of material burned
X
The forest fire emissions appear in Table V-l.
PROJECTION YEARS
The State Firewarden also supplied the tons of material burned in 1977
and estimates of the amount of forest material that will be consumed by fire
for 1982 and 1987. The above mentioned emission factors were also utilized
to calculate the future forest fire emissions.
OXIDANT SEASON
According to information supplied by the State Firewarden, 41.7% of the
annual forest fire emissions occurred in the oxidant season. Table IV-2 lists
the forest fire oxidant season emissions.
V-l
-------
TABLE V-l
ESTIMATED FOREST FIRE EMISSIONS
(TPY)
1975
VOC NO
X
Atlantic
Bergen
Burlington
Camden
Cape May
Cumberland
Essex
Gloucester
Hudson
Hunterdon
Mercer
Middlesex
Monmouth
Morris
Ocean
Fassaic
Salem
Somerset
Sussex
Union
Warren
130
3
125
64
53
,53
0
28
0
5
0
100
25
22
249
13
24
1
10
0
10
'22
+
21
11
9
9
0
5
0
1
0
17
4
4
41
2
4
+
2
0
2
1977
VOC NO
X
1032
23
994
505
419
419
0
225
0
39
. 0
792
201
174
1980
101
194
8
78
0
78
170
3
164
83
69
69
0
37
0
6
0
131
33
29
327
17
32
1
13
0
13
1982
VOC NO
X
335
9
422
214
79
493
-
95
-
16
-
336
86
74
729
43
82
3
33
-
33
55
2
69
35
13
81
-
16
-
3
-
55
14
12
120
7
14
+
5
-
5
1937
VOC NO
X
335
-
468
248
78
493
-
105
-
18
-
372
95
82
907
48
91
3
- -
-
36
55
-
77
41
13
82
-
17
-
3
-
62
16
14
150
8
15
+
6
-
6
State Total 915 155 7262 1197 3082 506 3145 565
+ less than 1 ton
- no fires projected
V-2
-------
TABLE V-2
ESTIMATED FOREST FIRE OXIDANT SEASON EMISSIONS
1975
Atlantic
Bergen
Burlington
Camden
Cape May
Cumberland
Essex
Gloucester
Hudson
Hunterdon
Mercer
Middlesex
Monmouth
Morris
Ocean
Passaic
Salem
Somerset
Sussex
Union
Warren
VOC
54
1
52
27
22
22
0
12
0
2
0
42
10
9
104
5
10
+
4
0
4
NO
X
9
+
9
5
4
4
0
2
0
+
0
7
2
2
17
1
2
+
1
0
1
(TPS)
1977
VOC
430
10
415
211
175
175
0
94
0
16
0
330
84
73
826
42
81
3
33
0
33
NO
X
71
1
68
35
29
29
0
15
0
3
0
55
14
12
136
7
13
+
5
0
5
1982
VOC
140
4
176
89
33
206
-
40
-
7
-
140
36
31
304
18
34
1
14
-
14
NO
X
23
1
29
15
5
34
-
7
-
1
-
23
6
5
50
3
6
+
2
-
2
1987
VOC
140
-
195
103
33
206
-
44
-
8
-
155
40
34
378
20
38
1
15
-
15
NO
X
23
^m
32
17
5
34
-
7
-
1
-
26
7
6
63
3
6
+
3
-
3
State Total 380
+ less than one ton
- no fires projected
66
3031
498
1287 212
1425
236
V-3
-------
CHAPTER VI
AGRICULTURAL BURNING
Agricultural burning emissions are composed of emissions from four
different categories: prescribed burning, infested burning, herbaceous burn-
ing, and orchard prunings burning. Agricultural burning was illegal in New
Jersey during 1975; therefore, the only component for the category of agri-
cultural burning during 1975 is prescribed burning.
BASE YEAR
The prescribed burning data came from the State Firewarden's Office; while
the infested, herbaceous, and orchard prunings data were obtained from open
burning permit applications for 1977 from the New Jersey Department of Environ-
mental Protection. The following assumptions, based on permit application data
and several conversations with NJDEP personnel, were made:
6 cords of wood per orchard pruning permit
10 acres of land per herbaceous burning permit
1 ton of material per infested burning permit
The following emission factors from AP-42 were utilized:
NO
Type of Burning VOC Emission Factor x
Prescribed 24 Ib/ton 4 Ib/ton
Orchard Prunings 9 Ib/ton
Herbaceous 85 Ib/ton
Infested 23 Ib/ton
It was assumed that only prescribed burning occurred in 1975 since other
types were disallowed by regulation. Evidence supporting this assumption is
based on conversations with several NJDEP ...air pollution control officials.
The annual agricultural burning emissions are listed in Table VI-1.
PROJECTION YEARS
A number of different methods were used to project future emissions from
this burning category. The actual projections for prescribed burning were
supplied by the State Firewarden's Office. The historical change in cropland
acreage, as noted in the 1974 New Jersey Census of Agriculture, was used to
VI-1
-------
generate an historical trend in acres of orchard, which was then utilized to
project pruning emissions.
OXIDANT SEASON
The percent of emissions which occurred in the oxidant season varied for
each of the four subcategories of agricultural burning. None of the pre-
scribed burning occurred in the oxidant season according to information supplied
by the State Firewarden. Permit applications to the NJDEP supplied the rest of
the oxidant season data which follows:
Subcategory Percent of Annual Emissions
Orchard Prunings 42.3
Infested 36
Herbaceous 31.6
The oxidant season emissions are listed in Table VI-2.
VI-2
-------
TABLE VI-1
Atlantic
Bergen
Burlington
Camden
Cape May
Cumberland
Essex
Gloucester
Hudson
Hunterdon
Mercer
Middlesex
Monmouth
Morris
Ocean
Passaic
Salem
Somerset
Sussex
Union
Warren
State Total
ESTIMATED AGRICULTURAL BURNING
(TPY)
19751 1977
VOC NO VOC NO
X X
33. 6 80 13
- - 2 +
202"- 34 " 183 30
+ +
24 4 ,- 38 6
16 3 23 3
_ _
16 1
- - - -
- - 3 +
- 1 +
- - 1 +
- - 3 +
11 +
151.. 25 172 28
+ +
- 8 +
- 7 +
- 7 +
- - - -
- - 5 +
426 72 560 81
EMISSIONS
1982
VOC NO
X
201 33
2 +
383 64
+ +
65 11
80 13
-
9 +
-
3 +
2 +
1 . +
9 1
12 +
239 40
+ +
7 +
7 +
9 +
-
8 +
1037 162
1987
VOC
268
3
527
+
64
79
-
8
-
3
1
1
2
12
218
+
6
8
9
-
8
1217
NO
X
44
+
87
+
11
13
-
+
-
+
+
+
+
+
36
+
+
+
+
-
+
193
Prescribed Burning only.
2 - no burning occurred
3 + less than one ton
VI-3
-------
TABLE VI-2
ESTIMATED AGRICULTURAL
1975
VOC
Atlantic + 2
Bergen +
Burlington +
Camden +
Cape May +
Cumberland +
Essex +
Gloucester +
Hudson +
Hunterdon +
Mercer +
Middlesex +
Monmouth +
Morris +
Ocean +
Passaic +
Salem +
Somerset +
Sussex +
Union +
Warren +
BURNING OXIDANT
(TPS)
1977
VOC
1.0
0.7
1.0
0.2
0.4
1.0
0
3.2
0
1.1
0.5
0.4
0.6
3.6
0.5
0.1
2.6
2.2 ,
2.6
0
1.7
SEASON EMISSIONS 1-
1982
VOC
1.0
0.7
0.9
0.2
0.3
0.9
0
3.0
0
1.3
0.5
0.4
0.6
3.2
0.6
0.1
2.3
2.4
3.5
0
1.6
1987
VOC
1.0
0.8
1.0
0.2
0.3
0.8
0
2.8
0
1.1
0.5
0.4
0.6
4.0
0.7
0.1
2.1
2.6
2.5
0
1.5
State Total + 23.4 23.5 23
1. NO emissions were negligible
2 + VOC emissions were less than .01 tons.
VI-4
-------
CHAPTER VII
STRUCTURAL FIRES
In New Jersey there is no requirement to report structural fires to any
state department or agency; therefore, the number of structural fires cited
in the New Jersey State Police Arson Squad newsletter are based solely on the
voluntary reporting of fires. Structural fire emissions depend upon the
quantity and type of material burned during a residential, commercial, or
industrial building fire.
BASE YEAR
The emissions from structural fires were calculated using the data found in
the "New Jersey Statewide Arson Network System Newsletter", July 1976 and
July 1978 issues. The number of fires for residences, mercantile establishments,
and industrial structures were totaled for each county. It was assumed that
each fire consumed an average of 25tons of material and that the material was
similar to municipal waste in character. The emission factors from AP-42 were
30 pounds per ton of material burned for volatile organic compounds and 6
pounds per ton of material burned for oxides of nitrogen. The emissions for
structural fires are listed in Table VII-1.
PROJECTION YEARS
The 1982 and 1987 emissions were projected from 1975 based on expected
population growth within each county.
OXIDANT SEASON
Based on information supplied from the Newark Fire Department, 48% of
structural fire emissions occurred in the oxidant season. Oxidant season
emissions are listed in Table VII-2.
In an Engineering-Science summary report, "An Air Quality Study for Revision of
the State Implementation Plan in Southern New Jersey", October 1976, the weight
of wood in a 1500 square foot single family dwelling was calculated to be 20.8
tons. To this total, 4.2 tons were, added to account for,the weight of home
furnishings.
VII-1
-------
TABLE VII-1
ESTIMATED -STRUCTURAL FIRE EMISSIONS
(TPY)
Atlantic
Bergen
Burlington
Camden
Cape May
Cumberland
Essex
Gloucester
Hudson
Hunterdon
Mercer
Middlesex
Monmouth
Morris
Ocean
Passaic
Salem
Somerset
Sussex
Union
Warren
VOC
561
648
417
1121
66
153
1875
180
384
40
650
695
464
456
165
420
53
182
98
536
24
1975
NO
X
112
130
83
224
13
31
375
36
76
8
130
139
93
91
33
84
11
36
20
107
5
VOC
570
566
498
356
123
232
2205
77
1995
43
159
854
600
305
171
320
104
284
108
311
51
1977
NO
X
114
113
100
71
25
46
441
16
399
9
32
171
120
61
34
64
21
57
21
62
10
VOC
705
668
480
1267
154
246
1898
222
1996
46
728
907
500
492
217
329
54
198
122
547
26
1982
NO
X
141
134
96
253
31
49
380
44
399
10
146
182
100
98
43
66
11
39
24
109
5
1987
VOC
861
682
501
1314
194
264
1914
235
1996
49
752
959
526
517
252
338
55
210
138
554
"
NO
X
172
137
100
263
39
52
383
47
399
10
150
192
105
103
50
68
11
42
28
111
6
State Total
9188
1837 9932
1987 11802
2360 12338
2468
VII-2
-------
TABLE VII-2
ESTIMATED STRUCTURAL FIRE OXIDANT SEASON EMISSIONS
1975
Atlantic
Bergen
Burlington
Camden
Cape May
Cumberland
Essex
Gloucester
Hudson
Hunterdon
Mercer
Middlesex
Monmouth
Morris
Ocean
Passaic
Salem
Somerset
Sussex
Union
Warren
VOC
269
311
200
538
32
73
900
86
184
19
312
334
223
219
79
202
25
87
47
257
11
NO
X
54
62
40
107
6
15
180
17
36
4
62
67
45
44
16
40
5
17
10
51
2
(TPS)
1977
VOC
274
272
239
171
59
111
1058
37
958
21
76
410
288
146
82
154
50
136
52
149
24
NO
X
55
54
48
34
12
22
212
8
191
4
15
82
58
29
16
31
10
27
10
30
5
1982
VOC
338
321
230
608
74
118
911
107
958
22
349
435
240
236
104
158
26
95
59
263
12
NO
X
68
64
46
121
15
23
182
21
191
5
70
87
48
47
21
32
5
19
11
52
2
1987
VOC
413
327
240
631
93
127
919
113
958
23
361
460
252
248
121
162
26
101
66
266
13
NO
X
83
66
48
126
19
25
184
23
191
5
72
92
50
49
24
33
5
20
13
53
3
State Total
4408
880
4767
953
5664
1130
5920
1184
VII-3
-------
CHAPTER VIII
NATURAL SOURCE EMISSIONS
There is a general lack of knowledge about natural source emissions which
will limit the accuracy of any inventory attempt. The emissions from natural
sources are just now becoming quantified and classified. Such sources as
natural seeps, sanitary landfills, animal wastes, forests, lawn and garden
vegetation, agricultural cropland, orchards, and pasture land should be in-
cluded in an inventory. However, the lack of emission information and the
difficulty in quantifying the amount of material in question prohibit the
inclusion of most of these categories.
BASE YEAR
An attempt to inventory three categories of natural emission sources has
been made. The sources include forests, pasture land, and agricultural crop
land. The following emission factors, which were based on information sup-
plied by P. R. Zimmerman from Washington State University, are actually the
emission factors for California hardwoods, California pines, California bush,
and Florida pasture land:
Component VOC Emissions
Non-pine trees .02 ton/acre year
Pine trees .1 ton/acre year
Harvested crop land .08 ton/acre year
Pasture land .004 ton/acre year
It must be remembered that emissions vary among species, with temperature,
with quantity of light received, and with geographical location.
The total acres of forest and percent pine trees per county were taken
from The Timber Resources of New Jersey. It was assumed that all pine trees
would emit volatile organic compounds at the same rate and all non-pine trees
would do the same.
The number of harvested acres per county was found in the 1974 New Jersey
Census of Agruculture. The assumption that an average emission factor for all
types of crops in New Jersey could be represented by one emission factor was
made. The California bush emission factor was chosen to represent this cate-
gory because it represented an average emission factor for small plants.
VIII-1
-------
The quantity of grass land per county was based on information supplied
in the 1974 New Jersey Census of Agriculture. The pasture land in Florida was
assumed to be similar to the pasture land in New Jersey.
Annual natural source emissions are listed in Table VIII-1.
PROJECTION YEARS
Projections for each category were handled separately. Historical trends
were used in all three instances.
Forest emissions were projected from the change in forest acreage in
New Jersey. The Timber Resources of New Jersey was the source of information
for this projection.
The source of historical data for agricultural crops was the 1974 New
Jersey Census of Agriculture. The change in harvested crop land served as
the basis for projections.
Pasture projected emissions came from information supplied in the 1974
New Jersey Census of Agriculture. The number of farm acres which were not
included in the harvested acres represented the pasture land for this report.
OXIDANT SEASON
Based on a discussion with P. R. Zimmerman, it was assumed that 100% of
the non-pine tree emissions, 90% of the pine tree emissions, 100% of the crop
land emissions, and 75.1% of the pasture land emissions occurred in the oxi-
dant season. Natural Source emissions for the oxidant season are listed in
Table VIII-2.
VIII-2
-------
TABLE VIII-1
ESTIMATED NATURAL SOURCE EMISSIONS
Atlantic
Bergen
Burlington
Camden
Cape May
Cumberland
Essex
Gloucester
Hudson
Hunter don
Mercer
Middlesex
Monmouth
Morris
Ocean
Passaic
Salem
Somerset
Sussex
Union
Warren
1975
VOC
9,940
1,020
15,153
3,443
3,845
8,537
1,302
3,063
1,642
3,295
1,859
2,278
5,360
4,596
14,174
2,164
3,396
2,606
5,824
1,050
3,537
(TPY)
1977
VOC
9,880
893
15,174
3,363
3,792
6,518
1,433
3,027
1,806
3,340
1,834
2,299
5,381
4,718
14,245
1,977
3,428
2,598
5,760
978
3,559
1982
VOC
9,490
642
14,880
3,116
3,588
6,326
1,580
2,886
1,986
3,417
1,755
2,322
5,326
4,999
14,126
1,612
3,463
2,539
5,478
819
3,561
1987
VOC
9,181
461
14,772
2,915
3,418
6,187
1,748
2,771
2,185
3,550
1,688
2,362
5,322
5,449
14,235
1,384
3,544
2,494 •
5,251
685
3,600
State Total
98,084
96,003
93,911
93,202
VIII-3
-------
TABLE VIII-2
ESTIMATED NATURAL
SOURCE OXIDANT
SEASON EMISSIONS
(IPS)
Atlantic
Bergen
Burlington
Camden
Cape May
Cumberland
Essex
Gloucester
Hudson
Hunterdon
Mercer
Middlesex
Monmouth
Morris
Ocean
Passaic
Salem
Somerset
Sussex
Union
Warren
State Total
1975
VOC
9,326
1,020
14,112
3,266
3,664
6,164
1,302
2,950
1,642
3,236
1,837
2,247
5,073
4,535
13,191
2,139
3,259
2,561
5,705
1,050
3,473
91,752
1977
VOC
9,269
893
14,140
3,187
3,612
6,148
1,432
2,915
1,806
3,284
1,813
2,268
5,096
4,657
13,266
1,953
3,293
2,554
5,643
978
3,497
91,704
1982
VOC
8,902
642
13,889
2,947
3,415
5,972
1,578
2,780
1,986
3,368
1,736
2,293
5,054
4,941
13,184
1,588
3,337
2,498
5,369
819
3,505
89,803
1987
VOC
8,612
461
13,812
2,751
3,251
. 5,845
1,744
2,670
2,185
3,505
1,671
2,334
5,060
5,394
13,321
1,361
3,424
2,456
5,148
685
3,548
89,238
VIII-4
-------
CHAPTER IX
SURFACE COATINGS
Surface coating emissions include architectural surface coating, automo-
bile refinishing, and other nonindustrial surface coatings.
BASE YEAR
Several approaches to divide surface coating into the three component
parts were attempted. Two surveys of automobile refinishing establishments,
one in South Carolina and the other one in Kentucky, gave annual emission
results of 12 tons per shop and 3.9 tons per shop, respectively. Two California
studies showed annual emission rates of 3.3-3.7 tons per 1,000 people for
architectural surface coating. Another California study gave an annual domestic
solvent emission rate of 1 ton per 1,000 people. The National Paint and Surface
Coating Manufacturers Association no longer generates estimates of the national
trade paint usage, from which a national solvent usage for trade paints could
be derived.
For the purposes of this study, the emission factor suggested in EPA
450/2-77-028 of 1.75 tons per 1,000 people per year was selected. This selection
was made because of the questionable results of the automobile refinishing sur-
veys, the difference in life styles between New Jersey and California, and the
incompatibility of the other emission factors with the EPA 450/2-77-028 suggest-
ed emission factor. The surface coating emissions are listed in Table IX-1.
PROJECTION YEARS
The projections for surface coatings were based on population changes re-
lative to the 1975 base year.
OXIDANT SEASON
The oxidant season emissions were assumed to be 100% of the annual surface
coating emissions, based on the concept that most solvent based coatings were
applied during the most favorable weather conditions which occur in the oxi-
dant season. The oxidant season emissions for surface coatings are listed in
Table IX-2.
IX-1
-------
TABLE IX-1
ESTIMATED SURFACE COATING EMISSIONS
(TPY)
Atlantic
Bergen
Burlington
Camden
Cape May
Cumberland
Essex
Gloucester
Hudson
Hunterdon
Mercer
Middlesex
Monmouth
Morris
Ocean
Passaic
Salem
Somerset
Sussex
Union
Warren
1975
VOC
329
1607
603
843
127
231
1642
333
1066
137
560
1091
850
712
514
830
109
370
173
964
140
1977
VOC
344
1621
659
910
137
236
1649
382
1066
141
601
1118
869
728
561
839
109
380
186
970
144
1982
VOC
413
1657
695
953
172
250
1662
412
1066
150
627
1187
915
768
676
862
110
403
215
983
150
1987
VOC
505
1692
725
988
216
268
1676
435
1067
160
648
1256
963
807
785
886
113
427
244
997
157
State Total
1
13231
13650
14326
15015
This includes surface coating, auto refinishing, and other non-industrial
coatings.
IX-2
-------
TABLE IX-2
ESTIMATED SURFACE COATING OXIDANT SEASON EMISSIONS
(TPS)
Atlantic
Bergen
Burlington
Camden
Cape May
Cumberland
Essex
Gloucester
Hudson
Hunterdon
Mercer
Middlesex
Monmouth
Morris
Ocean
Passaic
Salem
Somerset
Sussex
Union
Warren
1975
VOC
329
1607
603
843
127
231
1642
333
1066
137
560
1091
850
712
514
830
109
370
173
964
140
1977
VOC
344
1621
659
910
137
236
1649
382
1066
141
601
1118
869
728
561
839
109
380
186
970
144
1982
VOC
413
1657
695
953
172
250
1662
412
1066
150
627
1187
915
768
676
862
110
403
215
983
150
1987
VOC
505
1692
725
988
216
268
1676
435
1067
160
648
1256
963
807
785
886
113
427
244
997
157
State Total 13231 13650 14326 15015
This includes surface coating, auto refinishing, and other non-industrial
coatings.
IX-3
-------
CHAPTER X
INCINERATORS
Incinerator emissions are a function of the quantity of material burned,
the type of material burned, and the design of the incinerator utilized. For
the purposes of this study, it was assumed that only commercial and pathol-
ogical wastes existed and that a correctly designed incinerator was used for
burning.
BASE YEAR
ES found that potential sources of information on incineration operation
were limited. A thorough investigation of the New Jersey Department of
Environmental Protection's records would have given the best data, but such
a survey was beyond the scope of this study. A quick survey of the data in
NJDEP's regional offices was conducted to get some idea of the concentration
of incinerators; however, this investigation was of limited value. A previous
study, in which ES conducted a survey of the NJDEP records for incinerators
in Atlantic, Cape May, Cumberland, and Ocean Counties, turned out to be the
best source of data.
The results of the previous study assisted in making estimates of state-
wide solid waste incineration. For the four county area in the previous study,
a waste incineration rate per employee was determined separately for pathologi-
cal and commercial waste incinerators. The amount of waste incinerated in 1975
was linearly interpolated from the data in the previous ES study. Utilizing
the number of retail and wholesale employees from the references noted in
Chapter II and the number of hospital employees from County Business Patterns
1976 New Jersey, the following average waste factors were developed for 1975:
Type of Waste Average Waste Burned
Commercial 0.2149 tons per retail or wholesale employee
Pathological 0.0706 tons per hospital employee
The following emission factors from AP-42 were applied to the tons of
waste calculated for each county:
X-l
-------
Type of Waste VOC Emissions NO Emissions
x
Commercial 3 Ibs/ton waste 3 Ibs/ton waste
Pathological Negligible 3 Ibs/ton waste
The annual incinerator emissions are listed in Table X-l.
PROJECTION YEARS
The commercial waste emissions were projected from 1975 using the re-
tail and wholesale employment changes noted in Chapter II. The pathological
waste emissions were projected from 1975 in proportion to the forecast popu-
lation changes.
OXIDANT SEASON
The lack of knowledge concerning incinerator use made it difficult to
apportion the annual emissions to the oxidant season. After considering
retail sales fluctuations and seasonal use of disposable items, a simple
assumption that 50% of the incinerator emissions occurred in the oxidant
season was made. The oxidant season emissions are listed in Table X-2.
X-2
-------
TABLE X-l
ESTIMATED INCINERATOR EMISSIONS
(TPY)
1975
Atlantic
Bergen
Cape May
Cumberland
Essex
Hudson
Hunterdon
Middlesex
Monmouth
Morris
Ocean
Passaic
Somerset
Sussex
Union
Warren
VOC
8.2
33.2
3.4
2.2
56.5
14.4
1.7
17.4
11.3
8.7
1.9
13.7
5.3
1.4
18.6
1.7
NO
X
8.2
33.9
3.4
2.4
57.8
15.1
1.8
17.5
11.9
9.2
1.9
14.2
5.6
1.5
19.2
1.8
1977
VOC
8.9
35.9
4.2
2.5
58.2
15.0
1.8
18.4
11.8
9.1
2.0
14.3
5.7
1.6
19.9
1.8
NO
X
8.9
36.7
4.2
2.6
59.6
15.7
1.9
18.5
12.3
9.6
2.0
14.8
6.0
1.7
20.5
1.9
1982
VOC
10.4
41.3
4.5
3.0
59.0
15.8
2.0
20.7
12.8
10.0
2.5
15.5
6.6
1.8
22.0
2.0
NO
X
10.4
42.1
4.6
3.2
60.3
16.5
2.1
20.8
13.4
10.6
2.5
16.0
6.9
1.9
22.6
2.1
1987
VOC
11.8
44.6
5.3
3.7
54.2
15.5
2.2
23.0
13.9
10.9
3.0
16.1
7.2
2.0
22.4
2.1
NO
X
11.8
45.4
5.3
3.9
55.6
16.2
2.3
23.1
14.5
11.4
3.0
16.6
7.6
2.1
23.0
2.2
X-3
-------
TABLE X-2
ESTIMATED INCINERATOR OXIDANT SEASON EMISSIONS
(TPS)
1975
Atlantic
Bergen
Cape May
Cumberland
Essex
Hudson
Hunterdon
Middlesex
Monmouth
Morris
Ocean
Passaic
Somerset
Sussex
Union
Warren
VOC
4.1
16.6
1.7
1.1
28.2
7.2
0.8
8.7
5.6
4.3
0.9
6.8
2.6
0.7
9.3
0.8
NO
X
4.1
16.6
1.7
1.2
28.9
7.5
0.9
8.7
5.9
4.6
0.9
7.1
2.8
0.7
9.6
0.9
1977
VOC
4.4
17.9
2.1
1.2
29.1
7.5
0.9
9.2
5.9
4.5
1.0
7.1
2.8
0.8
9.9
0.9
NO
X
4.4
18.3
2.1
1.3
29.8
7.8
0.9
9.2
6.1
4.8
1.0
7.4
3.0
0.8
10.2
0.9
1982
VOC
5.2
20.6
2.2
1.5
29.5
7.9
1.0
10.3
6.4
5.0
1.2
7.7
3.3
0.9
11.0
1.0
NO
X
5.2
21.0
2.3
1.6
30.1
8.2
1.0
10.4
6.7
5.3
1.2
8.0
3.4
0.9
11.3
1.0
1987
VOC
5.9
22.3
2.6
1.8
27.1
7.7
1.1
11.5
6.9
5.4
1.5
8.0
3.6
1.0
11.2
1.0
NO
X
5.9
22.7
2.6
1.8
27.8
8.1
1.1
11.5
7.2
5.7
1.5
8.3
3.8
1.0
11.5
1.1
X-4
-------
CHAPTER XI
OPEN BURNING
The emissions included in this category are from fire training exercises.,
land clearing operations, and the illegal burning of solid waste. All open
burning was illegal in New Jersey during 1975 with the exception of fire train-
ing.
BASE YEAR
Available information for open burning is very limited. A telephone survey
of the New Jersey Department of Environmental Protection's regional offices was
conducted to get a general feeling for the frequency of illegal open burning in
each area of the state. The results of the survey indicated that no significant
amount of open burning occurred in 1975. Land clearing permit summaries from
the NJDEP were consulted, but data on the amount of land clearing waste burned
was not available. A telephone survey of the major fire training centers pro-
vided the only tangible data for this category. Officials at the centers sup-
plied E-S with fuel types and quantities used in fire training exercises.
The JP-4 emission factor from Air Pollution Emissions for JP-4 Fires Used
in Fire Fighting Training was utilized. After looking at emission factors from
a variety of combustion sources and finding nothing appropriate to use, calculated
emission factors for gasoline and No. 2 fuel oil were used. The gasoline and No.
2 fuel oil emission factors were based on the ratio of the vapor pressure of gaso-
line or No. 2 fuel oil to the vapor pressure of JP-4. This ratio was then multi--
plied by the emission factor for JP-4. The emission factors are as follows:
Fuel VOC Emissions NO Emissions
~ x
JP-4 467.2 Ibs/lOOOgallons 19.2 lbs/1000 gallons
Gasoline 1868.8 lbs/1000 gallons 76.8 lbs/1000 gallons
No. 2 fuel oil 2.7 lbs/1000 gallons .1 lbs/1000 gallons
The emissions for open burning include only the emissions from fire training and
are listed in Table XI-1.
PROJECTION YEARS
With the exception of two counties, emission projection factors were diffi-
cult to locate for this category. Because fire training is the result of a
people intensive activity parameter, housing and aircraft operations, population
XI-1
-------
TABLE XI-1
Atlantic
Bergen
Cape May
Cumberland
Essex
Hudson
Hunterdon
Middlesex
Monmouth
Morris
Ocean
Passaic
Somerset
Sussex
Union
Warren
1
ESTIMATED OPEN BURNING EMISSIONS
(TPY)
1975 1977 1982 1987
VOC NO VOC NO VOC NO VOC NO
X X X X
4.7 0.2 4.7 0.2 5.6 0.2 6.9 0.3
1.3 0.1 1.3 0.1 1.3 0.1 1.4 0.1
- - - - - - -
--------
7.5 0.3 7.5 0.3 7.6 0.3 7.6 0.3
________
________
________
3.3 0.1 3.3 0.1 3.3 0.1 3.3 0.1
________
2.0 0.1 2.0 0.1 2.7 0.1 2.7 0.1
- _._
________
--------
_ _ _ _ _ _ _
--------
Firetraining emissions are the only significant emissions for this category.
XI-2
-------
was chosen as the projection method. In Monmouth County the U.S. Navy sees no
increase in emissions over the 1975 levels. In Ocean County the U.S. Navy
expects to use 3000 more gallons of fuel in 1982 and 1987 than was used in 1975
or 1977.
OXIDANT SEASON
Based on data from the fire training centers, 90% of the annual emissions
from fire training occurred in the oxidant season. However, the U.S. Navy in-
dicated that in Monmouth County 50% of the annual emissions occurred in the
oxidant season. The oxidant season open burning emissions are listed in Table
VI-2.
XI-3
-------
TABLE XI-2
Atlantic
Bergen
Cape May
Cumberland
Essex
Hudson
Hunterdon
Middlesex
Monmouth
Morris
Ocean
Passaic
Somerset
Sussex
Union
Warren
ESTIMATED OPEN BURNING OXIDANT SEASON EMISSIONS
(TPS)
1975 1977 1982 1987
VOC NO VOC NO VOC NO VOC NO
X X X X
4.2 0.2 4.2 0.2 5.0 0.2 6.2 0.3
1.2 0.1 1.2 0.1 1.2 0.1 1.3 0.1
--------
________
6.8 0.3 6.8 0.3 6.8 0.3 6.8 0.3
_ _ _ _ _ _
--------
________
1.7 0.1 1.7 0.1 1.7 0.1 1.7 0.1
________
1.8 0.1 1.8 0.1 2.4 0.1 2.4 0.1
_._ _ _ _ _ _
_ _-_
__ _ _
________
________
XI-4
-------
CHAPTER XII
RAILROADS
Railroad emissions depend upon the amount of fuel burned by passenger trains,
freight trains, switch engines, and idling locomotives. A detailed inventory of
fuel use from the railroad companies operating in Warren, Sussex, and Hunterdon
Counties were attempted but were abandoned because of incomplete data.
BASE YEAR
Information on railroad fuel usage was obtained from two sources. Engineer-
ing-Science, in a previous study for New Jersey, conducted a survey of 1974
fuel use for the railroads operating in Atlantic, Cape May, Cumberland, and Ocean
Counties. The 1975 fuel usage for these four counties was obtained through
linear interpolation of the previous Engineering-Science data. For the remain-
ing three counties, the state distillate fuel oil usage for railroads from the
1975 Mineral Industry Survey was proportioned to each county based on the percent
of railroad track in that county as determined from the Yearbook of Railroad Facts
1976 and U. S. Geological Survey maps of New Jersey.
The emissions factors for railroads from AP-42 were 94 pounds per 1,000
gallons of fuel for volatile organic compounds and 370 pounds per 1,000 gallons
of fuel for oxides of nitrogen. The resulting railroad emissions by county
are listed in Table XII-1.
PROJECTION YEARS
The projection year data came from two sources. The fuel usage for
Atlantic, Cape May, Cumberland, and Ocean Counties was again calculated by
using linear interpolation of data from the previous Engineering-Science
study. For Warren, Sussex, and Hunterdon Counties a 1% per year growth rate
was assumed, consistent with the recommendation of the New Jersey Department
of Transportation. Engineering-Science made use of the base year emission
factors in estimating the projection year emissions shown in Table XII-1.
XII-1
-------
TABLE XII-1
ESTIMATED RAILROAD EMISSIONS
1975
VOC
H Atlantic 4 •
to
Cape May 3
Cumberland 7
Hunterdon 94
Ocean 6
Sussex 80
Warren 124
NO
X
18
13
26
371
22
313
487
(TPY)
1977
VOC
4
4 ,
7
96
6
81
126
NO
X
17
14
27
378
23
319
497
1982
VOC
4
4
7
101
6
85
133
NO
X
17
15
28
398
25
336
522
1987
VOC
4
4 '
8
106
7
90
139
NO
X
17
16
30
418
27
353
549
-------
OXIDANT SEASON
The effects of the summer tourist activity on passenger train service in
the resort areas were estimated from information received during the previous
Engineering-Science fuel survey from Pennsylvania-Reading Seashore Lines. Based
on this data, 53.3% of the annual emissions for Atlantic County occurred in
the six month oxidant season. For Cape May County, 53% of the annual emissions
occurred in the oxidant season. These figures show that tourist trade does not
significantly effect railroad emissions during the oxidant season.
In the remaining counties it was assumed that 50% of the annual emissions
occurred in the oxidant season. The oxidant season emissions are listed in
Table XII-2.
XII-3
-------
TABLE XII-2
ESTIMATED
RAILROAD OXIDANT
SEASON
EMISSIONS
(TPS)
1975
Atlantic
Cape May
Cumberland
Hunterdon
Ocean
Sussex
Warren
VOC
2
2
3
47
3
40
62
NO
X
9
7
13,
185
11
156
243
1977
VOC
2
2 '
3
48
3
40
63
NO
X
9
7
13
189
1]
159
248
1982
VOC
2
2
3.
50
3.
42
66
NO
X
9
8
14 (•
119.
12.
168
261 '
1987
VOC
2.
2
4
53
3
45
69.
NO
X
9.
8.
15 . .;
209,.
13.
176
274
XII-4
-------
CHAPTER XIII
AIRCRAFT
This category includes aircraft emissions occurring during the following
cycle: taxi-idle, takeoff, climbout, approach, and taxi-idle. Volatile organic
compound emissions at airports from space heating and fuel transfer operations
are not included in this chapter.
BASE YEAR
Information on aircraft operations came from several sources. The majority
of the information came from the "New Jersey State Airport System Plan"
developed by the New Jersey Department of Transportation, Division of Aviation
Planning. The NJDOT supplied operations data, projected operations for future
years, and forecasts of based aircraft by type for all nonmilitary airports in
the study area. The "Military Air Traffic Activity Report" 1975 and personal
communications with military personnel were the sources for operations and air-
craft mix for the military bases. The data for National Aviation Facilities
Experimental Center came from the NJDOT, personnel at NAFEC, the consulting
firm of Greiner Engineering Science. Both R. Dixon & Speas and Greiner En-
gineering Science are currently working on airport design changes for NAFEC.
The data provided by the NJDOT was interpolated to obtain operations and
aircraft mix for the years of interest. The number of operations was con-
verted to landing-takeoff cycles by assuming that one LTD equals two opera-
tions. It was also assumed that the percent of LTO's per aircraft type was
identical to the aircraft mix at the airport in question.
The emission factors listed in Table XIII-1 were utilized to calculate
emissions. The annual aircraft emissions are shown in Table XIII-2.
PROJECTION YEARS
Projection years emissions were determined from interpolations of projected
activity from the NJDOT information, and the future aircraft mix and operation
estimates supplied by military personnel, NAFEC personnel, R. Dixon & Speas, and
Greiner Engineering Science.
XIII-1
-------
TABLE XIII-1
AIRCRAFT EMISSION FACTORS
AIRCRAFT
Jumbo j et
Long range jet
Medium range jet
Air carrier turboprop
General aviation turboprop
General aviation piston
Helicopter
Military transport
Military jet
Military piston
VOC
(Ibs/engine/LTO)
12.2
41.2
4.9
2.9
1.1
0.4
0.52
2.7
9.93
20.4
NO
11 -X
(Ib/engine/LTO)
31.4
7.9
10.2
2.5
1.2
0.047
0.57
2.2
3.29
0.2
XIII-2
-------
TABLE XII1-2
ESTIMATED AIRCRAFT EMISSIONS1
(TPY)
1975 1977
VOC NO VOC NO
X X
Atlantic 1134 552 1141 554
Cape May 6 1 81
Cumberland 16 . 16 17 16
Hunterdon 4 _^2 6 1
Ocean 487 21 488 21
Sussex 7 i 8 1
Warren 4 + 6. 1
1982 1987
VOC NO VOC NO
X X
160 145 121 149
11 1 11 1
23 24 23 24
8 1. 8. 1
533 18 529 15
9 1 9-1
12 1 12 - 1
The fluctuations in emissions are due to changes in aircraft mix,
aircraft operations, and new emission regulations.
+ the emissions are less than one ton per year.
XIII-3
-------
OXIDANT SEASON
From information supplied by NJDOT, it was determined that 54.8% of
the annual aircraft emissions for general aviation occurred in the oxidant
season. Because of the scheduled nature of commercial aviation and the
all weather mission of the military, it was assumed that 50% of their
emissions occurred in the oxidant season. The oxidant season emissions are
listed in Table XIII-3.
XIII-4
-------
TABLE XIII-3
ESTIMATED AIRCRAFT OXIDANT SEASON EMISSIONS
(TPS)
1975 1977
Atlantic
Cape May
Cumberland
Hunterdon
Ocean
Sussex
Warren
VOC
568
4
8
2
244
4
2
NO VOC NO
X X
277 572. 278
+ ' 4 +
898
+ 3 +.
11 245 11
+ 5 + '
+ 3 +
1982 1987
VOC
82
6
12
4
267
5
7
NO VOC NO
X X
73 6} 75
161
12 13 13
+ 4 +
9 265 7
+ 5 +
171
+ The emissions are less than one ton per year.
XIII-5
-------
TABLE XIV
VESSELS
This source category includes emissions from dry and liquid cargo vessels,
recreational boats, and miscellaneous vessels such as Coast Guard cutters, na-
val ships, ferries, and dredges.
BASE YEAR
The emissions for each type of vessel were computed separately. The annual
emissions listed in Table XIV-1 are a composite of the emissions from all ves-
sels considered in this study.
Cargo vessel fuel consumption was estimated from the ton-mile statistics*
available in the 1975 Waterborne Commerce of the United States - Part I Water-
ways and Harbors Atlantic Coast, and the 590 BTU/per ton-mile fuel requirement
from The Effect of Fuel Price Increases on Energy Intensiveness of Freight
Transport and Energy Intensiveness of Passenger and Freight Transport Modes.
The intracoastal cargo vessel emissions were proportioned to Ocean, Cape May,
and Atlantic Counties based on coastal distances. Emissions from vessels
passing through Delaware Bay were proportioned to Cumberland and Cape May
Counties based on the county's frontal distances along the bay. The emissions
for Delaware Bay were reduced by 67.5% to account for partial impaction due to
meteorological dispersion, based on information available from the U. S.
Weather Bureau in "Summary of Hourly Observations-Wilmington, Delaware" 1951-
1960. Vessel emissions released within a county's boundaries were considered
belonging exclusively to that county. Table XIV-2 summarizes the emissions
and fuel use for cargo vessels.
The number, size, and type of pleasure boats used in each county was from
information provided in the 1977 "Survey of New Jersey's Registered Motorboat
Fleet". The number of motorboats operating on lakes and rivers within a county
was increased by an assumed value of 20% to account for boats brought into the
county from other political subdivisions. The following assumptions were made
with regards to annual fuel consumption based on data in AP-42 :
Type of Ship Annual Fuel Use
Outboard-gasoline 160 gal/year
Inboard-gasoline 480 gal/year
Inboard-diesel 480 gal/year
XIV-1
-------
TABLE XIV-1
ESTIMATED VESSEL EMISSIONS
(TPY)
1975
Atlantic
Cape May
Cumberland
Hunterdon
Ocean
Sussex
Warren
VOC
798
994
280
534
3781
583
85
NO
X
92
255
183
3.
630
8
i ;
1977
VOC
835
1068
286
549
4125
626
, 87
NO
X
96
268
187
3 .
687
9
1
1982
VOC
1002
1335
303
585
4976
725
91
NO
X
116
315 '
197
3,
829
10
1
1987
VOC
1224
1673
325
623
5774
823
96
NO
X
141
372
208
4 -
962
11
1
Emissions from Delaware Bay apportioned to Cumberland and Cape May counties
based on annual windrose data.
XIV-2
-------
TABLE XIV-2
LOCATION'""
Ocean County:
Manas quan R.
Barnegat Inlet
Tucker ton Creek
Intracoastal
Atlantic County:
Absecon Creek
Absecon Inlet
Intracoastal
Cumberland County :
Cohansey River
Maurice River
Delaware Bay
Cape May County:
Cape May Canal
Intracoastal
Delaware Bay
EMISSIONS
TON-MILES
9,036
1,817
2,286
183,307.5
372
61,621
91,653.8
883,097
85,680
3.7 x 109
14,241
91,653.8
1.6 x 109
FROM CARGO VESSELS
FUEL
TYPE
D
D
D
D
D
D
D
D
D
R
D
D
R
FUEL
CONSUMED
(103 gal)
Negligible
Negligible
Negligible
0.77
Negligible-
0.26
0.4
3.7
0.36
14,553.4
0.1
0.4
6293.4
EMISSION
FACTORS
(lbs/103 gal)
NO VOC
x
23.6
23.6
23.6
23.6
23.6
23.6
23.6
23.6
23.6
55.8
23.6
23.6
55.8
3
3
3
3
3
3
3
3
3
.682
3
3
.682
TOTAL
EMISSIONS
(TPY)
NO VOC
x
Negligible
Negligible
Negligible
Negligible
Negligible
Negligible
Negligible
Negligible
Negligible
406 5.0
(132)1 (2.)
Negligible
Negligible
176 2.1
(57) (1.)
Values in parenthesis are reduced by 67.5% to account for partial impact.
XIV-3
-------
Table XIV-3 summarizes the fuel use and emissions for pleasure boats.
PROJECTION YEARS
All cargo vessel emissions were projected to increase 1% per year. The
pleasure boat emissions are expected to increase with the change in popula-
tion. The Cape May Ferry is expected to grow at a 1% per year rate.
OXIDANT SEASON
The Cape May Ferry does 60% of its annual business during the oxidant
season. Because of the regular nature of the cargo traffic, it was assumed
that 50% of the vessel emissions occurred between April and October, but only
36.3% of those emissions reached New Jersey based on wind conditions during
the oxidant season. EPA-600/4-77-041 suggests that 100% of the pleasure boat
emission occurred in the oxidant season. Table XIV-4 lists the oxidant sea-
son emissions for all vessels.
XIV-4
-------
TABLE XIV-3
EMISSIONS FROM
PLEASURE, CHARTER AND LIVERY BOATS BY COUNTY
COUNTY
NUMBER
OF
BOATS
FUEL
(103 gal)
OUTBOARD GASOLINE
Atlantic
Cape May
Cumberland
Hunterdon
Ocean
Sussex
Warren
Atlantic
Cape May
Cumberland
Hunterdon
Ocean
Sussex
Atlantic
Cape May
Cumberland
Hunterdon
Ocean
Sussex
Warren
8512
10079
2853
6065
39103
6600
960
552
1012
248
—
4545
—
856
1342
508
—
5711
56
— —
1362
1613
456
970
6256
1056
154
INBOARD GASOLINE
265
486
119
—
2182
—
INBOARD DIESEL
411
644
244
—
2741
27
— • —
EMISSION
FACTOR
(lbs/103 gal)
NO VOC
X
ENGINES
6.6
6.6
6.6
6.6
6.6
6.6
6.6
ENGINES
131
131
131
—
131
—
ENGINES
340
340
340
—
340
340
— —
1100
1100
1100
1100
1100
1100
1100
86
86
86
—
86
—
180
180
180
—
180
180
— • —
EMISSION
(TPY)
NO VOC
X
4.5
5.3
1.5
3.2
20.6
3.5
0.5
17.4
31.8
7.8
—
142.9
—
69.9
109.5
41.5
—
466.0
4.6
~~
749.1
887.2
250.8
533.5
3440.8
580.8
84.7
11.4
20.9
5.1
—
93.8
—
37.0
58.0
22.0
—
246.7
2.4
~~
XIV-5
-------
TABLE XIV-4
ESTIMATED VESSEL OXIDANT SEASON EMISSIONS
(TPS)
1975
VOC NO
1977
VOC
NO
1982
VOC NO
1987
VOC
NO
Atlantic
Cape May
Cumberland
Hunterdon
Ocean
Sussex
Warren
797.5
882.6
278.8
533.5
3781.0
583.0
84.7
91.8 834.2
209.3 1057.0
154.5 284.5
3.2 548.4
630.0 4125.0
8.1 626.0
0.5 86.8
96.0 1002.0
221.8 1324.0
157.7 302.1
3.3 584.2
687.0 4976.0
8.7 725.3
0.5 91.0
115.3 1223.0 140.8
256.3 1661.0 319.8
166.7 323.8 177.0
3.5 622.1 3.7
829.0 5774.0 962.0
10.1 822.6. 11.4
0.5 95.2 0.6
XIV-6
-------
CHAPTER XV
OFF-HIGHWAY VEHICLES
Off-highway vehicle emissions are composed of emissions from three cate-
gories: farm tractors, diesel construction equipment and general utility
engines. Each category has been addressed separately because the differing
methods used in calculating their emissions. The total annual emissions for
off-highway vehicles are listed in Table XV-1. The total oxidant season
emissions for off-highway are listed in Table XV-2.
GENERAL UTILITY ENGINES
General utility engines are a component of off-highway vehicle emissions.
This category includes those engines used on lawn mowers, garden tractors,
snow blowers, etc.
Base Year
By assuming 13 gallons of fuel per capita, from EPA 450/4-74-008, and
using the population data discussed in Chapter II, the annual fuel use per
county was calculated. AP-42 suggests using a breakdown of 10% two stroke
engines and 90% four stroke engines when applying the following annual fuel
usage to the following emission factors:
Type of Engine VOC Emissions NO Emissions
x
2 stroke 1.572 Ibs/gallon .0116 Ibs/gallon
4 stroke .3285 Ibs/gallon .0448 Ibs/gallon
The general utility engine annual emissions are listed in Table XV-3.
Projection Years
Future emissions from general utility engines were projected by using the
expected increase in population.
Oxidant Season
EPA-600/4-77-041 suggests that 100% of the annual emissions from this
category occurs in the oxidant season. This estimate was believed too high
because snow blower and chain saw emissions occur during the non-oxidant sea-
son. An assumption of 98% was utilized, when calculating the oxidant season
XV-1
-------
TABLE XV-1
ESTIMATED OFF -HIGHWAY VEHICLE EMISSIONS1
(TPY)
Atlantic
Gape May
Cumberland
Hunterdon
Ocean
Sussex
Warren
VOC
555
218
332
273
870
312
264
1975
NO
X
106
34
136
118
98
74
88
VOC
599
234
439
279
949
332
269
1977
NO
X
106
34
135
117
107
73
86
VOC
714
291
460
293
1144
379
278
1982
NO
X
112
38
131
115
126
71
82
1987
VOC
865
365
488
308
1326
425
288
NO
X
121
43
129
113
143
70
79
Includes farm tractor emissions, diesel construction equipment
emissions, and general utility engine emissions.
XV-2
-------
TABLE XV-2
ESTIMATED OFF-HIGHWAY VEHICLE OXIDANT SEASON EMISSIONS
(TPS)
1975
Atlantic
Cape May
Cumberland
Hunterdon
Ocean
Sussex
Warren
VOC
537
212
410
254
851
299
250
NO
X
87
29
102
86
92
58
66
1977
VOC
581
228
419
260
928
319
255
NO
X
88
30
102
85
99
58
65
1982
VOC
694
284
439
274
1119
366
265
NO
X
95
34
100
84
117
58
63
1987
VOC
843
356
467
289
1298
412
275
NO
X
107
39
99
83
134
59
60
XV-3
-------
TABLE XV-3
ESTIMATED
GENERAL UTILITY1'
ENGINE EMISSIONS
(TPY)
1975
Atlantic
Cape May
Cumberland
Hunterdon
Ocean
Sussex
Warren
VOC
533
213 '
388
231
865
291
235
NO
X
. 51
19
35
21
78
27:
21,
1977
VOC
578 ;
229
397
237 •
943
313
241
NO
X
53
21
36
22
86
29
22
1982
VOC
695'
287
421
253!
1138i
362
253
NO
X
63
26
38
23
104
33
23
1987
VOC N°x
848 78
362' 33
451 41
269 25
1320 121
411 38
265 24
A reduction in emissions based on regulation change was not considered in the estimation
of projected emissions.
-------
emissions for general utility engines.
FARM TRACTORS
Farm tractor emissions are another component of the off-highway vehicle,
emissions. Emissions from farm tractors are composed of the emissions from
gasoline and diesel powered tractors.
Base Year
To calculate farm tractor emissions an annual average fuel use per trac-
tor was needed. This was computed by taking the gallons of gasoline used on
farms in New Jersey, from the 1974 Highway Statistics, and the number of trac-
tors on New Jersey farms, from the 1974 New Jersey Census of Agriculture. By
assuming that 60% of the tractors in the state are gasoline, an annual average
fuel use of 427 gallons per tractor was calculated. The annual quantity of
gasoline and diesel fuel per county was computed by assuming all tractors used
427 gallons per year.
The 1974 fuel use was projected to 1975 by using the historical change in
the number of harvested acres from the 1974 New Jersey Census of Agriculture.
The following emission factors from AP-42 were applied:
Type of Tractor VOC Emissions NO Emissions
x
Diesel 60.7 lbs/1000 gallons 335 lbs/1000 gallons
Gasoline 125 lbs/1000 gallons 151 lbs/1000 gallons
Farm tractor emissions for 1975 are listed in Table XV-4.
Projection Year
The future emissions from tractors were projected by using an historical
trend found in the 1974 New Jersey Census of Agriculture. The change in
harvested cropland acreage was used to project emissions.
Oxidant Season
According to information supplied by EPA-450/3-75-078, 67% of the annual
tractor emissions occurred in the oxidant season.
XV-5
-------
TABLE XV-4
ESTIMATED FARM TRACTOR EMISSIONS
1.
(TPY)
1975
Atlantic
Cape May
Cumberland
Hunterdon
Ocean
Sussex
Warren
VOC
21.3
4.7
42.8
41.9
5.0
20.1
28.4
NO
X
48.2
10.6
96.8
94.8
11.3
45.6
64.2
1977
VOC
20.4
4.2
41.7
41.2
5.0
18.8
27.4
NO
X
46.2
9.4
94.3
93.3
11.3
42.5
62.0
1982
VOC
18.4
3.1
39.0
39.6
5.0
15.8
25.2
NO
X
41.5
7.1
88.3
89.6
11.3
35.8
56.9
1987
VOC
16.5
2.4
36.6
38.0
5.0
13.3
23.1
NO
X
37.4
5.3
82.8
86.1
11.3
30.1
52.3
A reduction in emissions based on regulation change was not considered
in the estimation of projected emissions.
XV-6
-------
CONSTRUCTION EQUIPMENT
Construction equipment is the final component of off-highway vehicle
emissions. The emissions from diesel construction equipment include the
emissions from bulldozers, graters, backhoes, scoopshovels, etc.
Base Year
To calculate diesel construction equipment fuel use, it was first neces-
sary to compute state diesel farm tractor fuel usage. This was done by assum-
ing 40% of the farm tractor noted in the 1974 New Jersey Census of Agriculture
were diesel powered. By using the annual average fuel use of 427 gallons per
tractor, the New Jersey state annual diesel farm tractor fuel use was de-
termined. This annual tractor fuel use was subtracted from the off-highway
diesel fuel use found in the 1975 "Mineral Industries Survey". The resulting
number of gallons were then attributed to diesel construction equipment for
the entire state.
The state-wide fuel usage was proportioned to the counties based on con-
struction employment. Emissions were calculated by applying an average emis-
sion factor from information supplied in AP-42. The emission factors were
29 pounds per 1000 gallons for volatile organic compounds and 407 pounds per
1000 gallons for oxides of nitrogen. The annual construction equipment emis-
sions are listed in Table XV-5.
Projection Years
Emissions for 1977, 1982, and 1987 were calculated based on the estimated
change in construction employment. The construction employment projections
for each county are noted in Chapter II.
Oxidant Season
Based on information supplied in EPA-600/4-77-041, it was assumed that
74.6% of the annual construction equipment emissions occurred in the oxidant
season.
XV-7
-------
TABLE XV-5
ESTIMATED DIESEL CONSTRUCTION EQUIPMENT EMISSIONS 1.
(TPY)
1975
Atlantic
Cape May
Cumberland
Hunterdon
Ocean
Sussex
Warren
VOC
0.5
0.3
0.3
0.2
0.6
0.1
0.1
NO
X
6.9
3.8
3.8
2.3
8.6
1.8
2.0
1977
VOC
0.5
0.3
0.3
.2
0.7
0.1
0.2
NO
X
6.8
4.0
4.0
2.3
9.2
1.9
2.2
1982
VOC
0.5
0.3
0.3
0.2
0.7
0.2
0.2
NO
X
6.5
4.4
4.4
2.2
10.1
2.2
2.4
1987
VOC
0.4
0.3
0.3
0.2
0.8
0.2
0.2
NO
X
5.7
4.6
4.5
2.3
10.7
2.2
2.4
* A reduction in emissions based on regulation change was not considered
in the estimation of projected emissions.
XV-8
-------
CHAPTER XVI
RESIDENTIAL HEATING FUEL
The emissions in this chapter result from the combustion process used
for space heating. Residential heating emissions include the emissions from
houses, apartment buildings, and condominiums.
BASE YEAR
The annual emissions listed in Table XVI-1 came from two sources. The
emissions listed for Atlantic, Cape May, Cumberland, and Ocean Counties
were the results of interpolating the fuel data from the previous ES study.
For Hunterdon, Sussex, and Warren Counties the method suggested in Volume
13 of EPA Guidelines for Air Quality Maintenance Planning and Analysis was
used to obtain fuel use estimates. The AP-42 emission factors used for
residential heating fuel are listed in Table XVI-2.
The base data for the Volume 13 procedures came from a number of sources.
The housing data came from the 1970 Census of Housing-Detailed Housing
Characteristics. The 5344 heating degree-day data for Allentown, Pennsylvania
came from the National Weather Service for the year 1975. To project the 1970
housing data to 1975 the population estimates noted in Chapter II were used along
with the population data available from the 1970 Census of Population - Num-
ber of Inhabitants - New Jersey. By assuming that the housing structure mix
would stay constant, that coal usage would not increase, and that new housing
units would be 40% electrical and 60% No. 2 fuel oil for space heating, the
fuel use estimates for the years of interest were computed for Hunterdon,
Warren, and Sussex Counties.
PROJECTION YEARS
Emissions for the projection years were handled in two different ways.
For Atlantic, Cape May, Cumberland, and Ocean Counties the fuel use results
of the previous ES study were interpolated for the years of interest before
applying emission factors. The remaining three counites required returning
to the method utilizated for the 1975 fuel use estimates. This time the
1977 degree-day information came from the National Weather Service, but the
1982 and 1987 degree-day data came from a 30-year summary for Allentown,
Pennsylvania.
XVI-1
-------
TABLE XVI-1
ESTIMATED RESIDENTIAL HEATING FUEL EMISSIONS
fTPY")
1975
Atlantic
Cape May
Cumberland
Hunterdon
Ocean
Sussex
Warren
VOC
29
14
27
14
44
16
15
NO
X
408
188
422
161
589
200;
173'
1977
VOC
29
15.
27
15 ,
46
17
16
NO
X
417
196
433
174
625
222 .
186
1982
VOC
30
17
29
16,
53
19
17
NO
X
441
221
466
187
733
255:
197
1987
VOC
32
18
31.
16
60
20
18 ,
NO
X
467
250
502
19S!
871
280
204;
XVI-2
-------
TABLE XVI-2
RESIDENTIAL HEATING FUEL EMISSION FACTORS
FUEL
VOC EMISSIONS
NO EMISSIONS
x
Anthracite Coal
Bituminous Coal
Distillate Fuel Oil
Residual Fuel Oil
Natural Gas
Wood
LPG
2.5 Ibs/ton
20 Ibs/ton
1 lb/103 gal
1 lb/103 gal
8 lbs/106 ft3
5 Ibs/ton
.7 lb/103 gal
3 Ibs/ton
3 Ibs/ton
18 lbs/103 gal
60 lbs/103 gal
80 lbs/106 ft3
1 Ib/ton
7 lbs/103 gal
XVI-3
-------
OXIDANT SEASON
The oxidant season emissions, listed in Table XVI-3, were based on
monthly heating degree-day information from Trenton and Atlantic City,
New Jersey. By assuming that the percent of heating degree-days which
existed from April 1 to October 1 were representative of the fuel use
during the oxidant season, it was estimated that 11.8% of the annual emis-
sions from Warren, Sussex, and Hunterdon Counties occurred in the oxidant
season. It was computed that 12.6% of the annual emissions from Atlantic,
Cape May, Cumberland, and Ocean Counties occurred in the oxidant season by
the same assumption.
XVI-4
-------
TABLE XVI-3
ESTIMATED RESIDENTIAL
HEATING FUEL OXIDANT SEASON EMISSIONS
(TPS)
1975
Atlantic
Cape May
Cumberland
Hunterdon
Ocean
Sussex
Warren
VOC
3.6
1.8
3.4
1.6
5.5
1.8
1.8
NO
X
51.4
23.6
53.1
19.1
74.2
23.6
20.4
1977
VOC NO
X
3.6
1.8
3.3
1.7
5.8
2.0
1.9
52.5
24.7
54.5
20.6
78.8
26.2
21.9
1982
VOC
3.8
2.0
3.6
1.8
6.6
2.2
2.0
NO
X
55.6
27.8
58.7
22.1
92.4
30.1
23.3
1987
VOC
4.0
2.3
3.8
1.9
7.6
2.4
2.0
NO
X
58.9
31.5
63.2
23.1
109.8
33.1
24.0
XVI-5
-------
CHAPTER XVII
COMMERCIAL FUEL
Emissions from this category include the emissions from fuel combustion
for space heating and process operations. The types of establishments in-
cluded in commercial fuel calculations were retail and wholesale businesses.
BASE YEAR
The fuel use emissions, listed in Table XVII-1, were determined in two
seperate procedures. The interpolated results of the fuel survey in the pre-
vious ES study provided fuel use estimates for Atlantic, Cape May, Cumberland,
and Ocean Counties.
The fuel estimates for Hunterdon, Sussex, and Warren Counties came from a
number of different sources. State-wide residual and distillate oil usage esti-
mates were the result of subtracting state-wide residential oil use from two
heating oil categories printed in a "Mineral Industry Survey" for 1975. A 1975
"MIS" publication was also the source of information for state-wide natural gas
usage. Based on information supplied by the NJDEP, it was assumed that no
commercial establishments burned coal in Hunterdon, Sussex, or Warren Counties.
The state-wide natural gas and oil use was apportioned to the three counties
based on retail-wholesale employment, as discussed in Chapter II.
Utilizing the fuel usage estimates for each county and the commercial fuel
emission factors, the annual commercial fuel emissions were calculated. The
following emission factors were based on information supplied in AP-42.
Fuel VOC Emissions NO Emissions
x
Anthracite Coal .375 Ibs/ton 14 Ibs/ton
Distillate Fuel Oil 1 lb/103 gal 22 lbs/103 gal
Residual Fuel Oil 1 lb/103 gal 60 lbs/103 gal
Natural Gas 8 lbs/166ft3 120 lbs/106ft3
PROJECTION YEARS
The emissions for 1977, 1982, and 1987 for Atlantic, Cape May, Cumberland,
and Ocean Counties were the result of interpolation from the previous ES study.
XVII-1
-------
TABLE XVII-1
ESTIMATED COMMERCIAL FUEL EMISSIONS
1975
Atlantic
Cape May
Cumberland
Hunterdon
Ocean
Sussex
Warren
VOC
16
4
14. ;
7:
8
6
7
NO*
351
109
568
212
147
180
a*
(TPY)
1977
VOC NOx
17 374
5 128
15 616
7 221
9, 158
7:. 196
8: 224
1982
VOC
19
5
19
8
10
8
8
NC^
429
134
733
246
183
228
245!
1987
VOC
21
6
22
9
11
8
91
N0,x
484
155
854
271 .
209
250
261
XVII-2
-------
For the remaining three counties, it was necessary to project emissions based
on expected changes in retail-wholesale employment.
OXIDANT SEASON
By assuming that process fuel use was insignificant, the percent of heating
degree-days in the oxidant season could be used to compute oxidant season emis-
sions. For the three northern counties 11.8% and for the southern four counties
12.6% of the annual emissions occurred in the oxidant season. These emissions
are listed in Table XVII-2.
XVII-3
-------
TABLE XVII-2
ESTIMATED COMMERCIAL FUEL OXIDANT SEASON EMISSIONS
(TPS)
1975
Atlantic
Cape May
Cumberland
Hunterdon
Ocean
Sussex
Warren
VOC
2.0
.5
1.7
.8
1.0
.7
.8
NO
X
44.2
13.7
71.6
25.1
18.5
21.2
25.3
1977
VOC
2.1
.5
1.9
.8
1.0
.7
.8
NO
X
47.1
16.1
77.7
26.2
19.8
23.1
26.5
1982
VOC NO
X
2.3
.6
2.3
.9
1.2
.9
.9
54.1
16.8
92.4
29.0
23.0
26.9
29.0
1987
VOC
2.6
.7
2.7
1.0
1.3
1.0
1.0
NO
X
60.9
19.5
107.6
32.0
26.3
29.5
30.9
XVII-4
-------
CHAPTER XVIII
LIGHT INDUSTRIAL FUEL
Industrial fuel emissions are labeled light industrial fuel emissions based
on the assumption that heavy industrial fuel usage was considered in the point
source emission inventory. Fuel use in this category is limited to small pro-
cesses and space heating.
BASE YEAR
The annual fuel use quantities for the seven counties came from different
sources. The source of fuel use data for Atlantic, Cape May, Cumberland, and
Ocean Counties was based on fuel survey noted in the previous ES study. The
results of the previous study had to be interpolated to obtain 1975 fuel use.
The fuel use data for Hunterdon, Warren, and Sussex Counties came from
"Mineral Industry Survey" data for 1975. The "MIS" data for anthracite coal,
bituminous coal, distillate oil, residual oil, and natural gas for New Jersey
was used in this study. The state-wide use of each fuel was apportioned to the
counties based on manufacturing employment in that county. The use of fuel by
point sources, from the NJDEP point source inventory, was subtracted from each
county's fuel allocations for all fuel categories. The resulting fuel inven-
tories served as the fuel use basis for calculating emissions.
Each county's annual fuel use inventory was then applied to the following
emission factors from AP-42:
FUEL VOC EMISSIONS NO EMISSIONS
A
Anthracite Coal .375 Ibs/ton 14 Ibs/ton
Bituminous Coal 1 Ib/ton 15 Ibs/ton
Distillate Oil 1 lb/10 gal 22 lbs/10 gal
3 3
Residual Oil 1 lb/10 gal 60 lbs/10 gal
£ O £ O
Natural Gas 3 lbs/10 ft 175 lbs/10 ft
The light industrial fuel emissions are listed in Table XVIII-1.
PROJECTION YEARS
Projection years emissions were computed in two ways. For Atlantic, Cape
May, Cumberland, and Ocean Counties interpolation of the fuel use data followed
XVIII-1
-------
TABLE XVIII-1
ESTIMATED LIGHT INDUSTRIAL FUEL EMISSIONS
(TPY)
1975
Atlantic
Cape May
Cumberland
Hunterdon
Ocean
Sussex
Warren
VOC
-
0.2
9.1
0.7
2.0
0.7
0.7
NO
X
0.8
7.0
402.8
36.3
84.0
30.2
14.9
1977
VOC
-
0.2
10.2
0.7
2.2
0.6
0.7
NO
X
1.0
7.5
507.0
36.1
89.0
28.5
15.0
1982
VOC NO
X
1.0
0.3 8.5
15.4 707.8
0.7 36.0
2.7 110.7
0.6 28.5
0.7 15.0
1987
VOC NO
X
-
0.3
18.0
0.7
3.2
0.6
0.7
1.2
9.4
826.1
36.0
111.6
28.5
15.8
- Emissions were less than .1 tons.
XVIII-2
-------
by application of the light industrial emission factors resulted in the projec-
tion emissions. For the remaining counties, emissions were projected based on
the expected change in manufacturing employment.
OXIDANT SEASON
Accessing oxidant season emissions for this category were difficult. The
emissions listed in Table XVIII-2 were based on the assumption that the most
significant percent of the emissions were due to space heating requirements.
By making this assumption, the heating degree-day method used in Chapter XVII
could be utilized again. In the three northern counties 11.8% of the annual
emissions occurred in the oxidant season. In the four southern counties 12.6%
of the annual emissions occured in the oxidant season.
XVIII-3
-------
TABLE XVIII-2
Atlantic
Cape May
Cumberland
Hunterdon
Ocean
Sussex
Warren
ESTIMATED LIGHT
1975
VOC NO
X
0.1
0.8
1.1 50.7
4.2
0.2 10.5
3.5
1.7'
INDUSTRIAL FUEL
(TPS)
1977
VOC NO
X
0.1
0.9
1.2 63.9
4.2
0.2 11.2
3.3
1.7
OXIDANT SEASON
1982
VOC NO
X
0.1
1.0
1.9 89.2
4.2
0.3 13.9
3.3
1.7
EMISSIONS
1987
VOC NO
X
0.1
1.1
2.2 104.1
4.2
0.4 14.0
3.3
1.8
- Emissions were less than .1 tons.
XVIII-4
-------
CHAPTER XIX
SLASH BURNING
The burning of wastes from logging operations is not permitted under
NJDEP regulations. Therefore, no emissions resulted from slash burning
operations in the base line year and none are projected.
XIX-1
-------
CHAPTER XX
COUNTY AND AQCR EMISSION SUMMARIES
Summarizing the results of a study which does not include every source
category for every county was not practical; however, one interesting point
was revealed. Before any comparison, it must be realized that the estima-
tion of natural source emissions is still in its infancy and that this
inventory did not include all anthropogenic sources of volatile organic
compound emissions. The emissions from natural sources in the southeastern
counties comprised roughly 70% of the estimated total emissions, while
natural sources accounted for approximately 52% of the emissions in the north-
eastern counties.
Tables XX-1 and XX-2 contain county emission summaries for both volatile
organic compounds and oxides of nitrogen. Tables XX-3 and XX-4 contain air
quality control region emission summaries for those New Jersey counties
noted in Table XX-5 for volatile organic compounds and oxides of nitrogen.
Appendices A and B contain the raw data necessary to calculate the area
source emissions for volatile organic compounds and oxides of nitrogen. The
•}
raw data has been displayed in National Emission Data Service format in Appen-
dix A and in tables by category and county in Appendix B.
XX-1
-------
TABLE XX-1
ESTIMATED TOTAL
1975
Atlantic
Bergen
Burlington
Camden
Cape May
Cumberland
Essex
Gloucester
Hudson
Hunter don
Mercer
Middlesex
Monmouth
Morris
Ocean
Passaic
Salem
Somerset
Sussex
Union
Warren
VOC
5,172
1,368
3,129
3,426
2,203
2,281
4,792
1,888
966
2,029
2,170
3,486
3,424
2,858
8', 041
2,179
936
1,520
2,284
2,583
1,473
NO
X
1,676
165
138
235
636
1,702
433
41
91
542
130
174
109
104
1,693
100
15
42
829
: 126
987
(TPY)
1977
VOC
4,827
4,514
4,265
. 3,293
2,805
2,840
5,284
2,144
3,577
. 2,179
1,805
4,505
3,938
3,032
10,254
2,270
1,225
1,734
2,536
.j 2,461
; 1,665
EMISSIONS 1
1982
NO
X
1,870
153
294
154
754
2,026
501
54
415
948
32
321
166
100
2,102
96
53
64
882
83
1,025
VOC
5,542
4,520
4,877
4,009
3,063
3,054
4,856
2,338
3,541
2,233
2,427
4,170
3,754
3,145
10,896
2,198
1,019
1,664
2,817
2,638
1,615
NO
X
1,501
178
229
288
792
2,433
441
60
416
1,002
146
258
129
121
2,230
89
25
46
961
133
1,077
1987
VOC
6,600
4,613
4,345
4,183
3,795
3,217
4,954
2,380
3,543
2,370
2,511
4,429
3,947
3,310
12,551
2,407
1,055
1,764
3,247
2,675
1,689
NO
X
1,663
183
264
304
915
2,714
439
64
415
1,053
150
277
137
128
1,615
93
26
50
1,031
134
1,126
State Total 58,208 9,968 71,153 12,093 74,376 12,555 79,585 12,781
Natural Source emissions were not included because of significant uncertainty
in the estimating procedures. Emissions were summed before rounding for each
county.
XX-2
-------
TABLE XX-2
ESTIMATED TOTAL OXIDANT
SEASON
EMISSIONS
1
(TPS)
1975
Atlantic
Bergen
Burlington
Camden
Cape May
Cumberland
Essex
Gloucester
Hudson
Hunterdon
Mercer
Middlesex
Monmouth
Morris
Ocean
Passaic
Salem
Somerset
Sussex
Union
Warren
State Total
VOC
3,632
1,984
2,065
2,349
1,746
1,741
3,390
1,360
1,568
1,599
1,518
2,809
2,491
2,055
5,912
1,754
654
1,106
1,824
1,943
1,097
44,597
NO
X
628
79
49
112
288
473
209
18
44
325
62
83
52
50
881
48
7
20
242
61
361
4,092
1977
VOC
4,203
3,438
2,621
2,315
2,168
2,010
3,656
1,511
2,368
1,694
1,381
3,322
2,764
2,168
8,06.4
1,708
793
1,229
1,994
1,905
1,198
52,510
NO
X
:• 701
74
116
69
344
529
242
23
199
332
15
146
78
46
1,072
75
23
31
296
40
375
4,826
1982
VOC
3,998
3,439
2,480
2,710
2,519
2,104
3,434
1,662
2,345
1,753
1,698
3,210
2,701
2,242
9,004
1,681
694
1,208
2,246
2,075
1,188
54,391
NO
X
498
86
75
136
367
592
213
28
200
345
70
121
61
57
1,169
43
11
22
311
64
384
4,853
1987
VOC
4,787
3,509
2 ,600
2,821
3,149
2,230
3,462
1,712
2,345
1,861
1,756
3,395
2,865
2,358
10,425
1,728
717
1,280
2,548
2,012
1,242
58,802
NO
X
564
89
80
143
447
635
212
30
200
358
72
130
64
61
1,355
44
12
24
330
65
400
5,315
Natural Source emissions were not included because of significant uncertainty
in the estimating procedures. Emissions were summed before rounding for each
county.
XX-3
-------
TABLE XX-3
ESTIMATED TOTAL EMISSIONS1
1975 1977 1982 1987
VOC N°x VOC N°x VOC N°x VOC N°x
Northeast
P ennsy1van ia-
Upper Delaware
Valley
Interstate
AQCR
(151) . 5,786 2,358 6,380 2,855 6,665' 3,040 7,306 3,210
New Jersey-
New York-
Connecticut
Interstate
AQCR
(043) 23,176 1,344 31,315 1,899 30,486 1,811 31,642 1,856
New Jersey
Intrastate
AQCR
(150) 17,697 5,707 20,726 6,752 22,555 6,956 26,163 6,907
Metropolitan
Philadelphia
Interstate
AQCR
(045) 11,549 559 12,732 587 14,670 748 14,474 808
State Total 58,208 9,968 71,153 12,093 74,376 12,555 79,585 12,781
Natural Source emissions were not included because of significant uncertainty
in the estimating procedures. Emissions were summed before rounding for each
county.
XX-4
-------
TABLE XX-4
ESTIMATED TOTAL OXIDANT SEASON EMISSIONS1
(TPS)
1975 1977 1982
VOC N°x VOC N°x VOC N°x
Northeast
Pennsylvania-
Upper
Delaware
Valley 4,520, 928 "4,886 1,003 .5,187 1,040
Interstate
AQCR
(151)
New Jersey-
New York-
Connecticut
Interstate
AQCR
(043) 19,100 646 22,553 901 22,335 867
New Jersey
Intrastate
AQCR
(150) 13,031 2,270 16,445 2,646 17,625 2,626
Metropolitan
Philadelphia
Interstate
AQCR
(045) 7,946 248 8,621 246 9,244 250
State Total 44,597 4,092 52,510 4,826 54,391 4,853
1987
VOC N°x
5,651 1,088
22,954 889
20,591 3,001
9,606 265
58,802 5,315
Natural Source emissions were not included because of significant uncertainty
in the estimating procedures. Emissions were summed before rounding for each
county.
XX-5
-------
TABLE XX-5
AIR QUALITY CONTROL REGIONS
AQCR NEW JERSEY COUNTIES
Northeast Pennsylvania Upper Delaware Valley Hunterdon
Interstate (151) Sugsex
Warren
New Jersey-New York-Connecticut Interstate (043) Bergen
Essex
Hudson
Middlesex
Monmouth
Morris
Passaic
Somerset
Union
New Jersey Interstate (150) Atlantic
Cape May
Cumberland
Ocean
Metropolitan Philadelphia Interstate (045) Burlington
Camden
Gloucester
i Mercer
Salem
XX-6
-------
APPENDIX A
NEDS FORMATED DATA
-------
AREA SOURCE
Input form
Slate
1
Year
ol
fecoiil
ioln
rs
3
[Q
County
1 1
*lto
AQCR
7 1 „ 1 ~
IL
particular
12
UJTiTlB 16
i£J£J
Name ol Person
EMISSION ESTIMATES (10?
S02
^Tio
19J20|21
I
NO,
22J2_3l24l25
_r tzs
26
tons)
27
'
HC
28[29J30
CO
31
IJ^ilL
32
33
34
35
SULFUR CONTENT (M
Anth. Bitum.
Coal Coal
36 17 38131
__JI
Disl.
Oil
40 J41
[
Resid
Oil
42J43
1
Com
ASH CONTENT |M
Anlh.
Coal
44|.isl46
i 1
Bitum.
Coal
47
48
,
49
Anth.
101 Ions
50U1J52J53
>ie!
nf
•oim
Oilumin.
I0>
54 55
Ions
^G
57
58
Date
RESIDENTIAL FUEL
Oisl. OH
104 Gal.
5960
._. ^
61
0
626
BH
Rtsid.
Oil
10'CJl.
) 64J65
66
67
~-t
68
0
Nat. Gas
107 II.3
69 70
71 £2 73
/Slop
Wood .
10? tons ' .
7JJ25J76|g
O
i!
78
•JA
"i
10
ioTTT
i
IVnlh.
I Ions
12
13
14
B
COM
Bilumin.
101 Ions
I?
ON SITi
Residential
10 1 Ions
10J11
I
12
13
14
15
16
17
i8pi9
i
IER£ IAL AND
Disl.Oil
10* Gals.
?0
. INCINERATION
Indus In »l
10? toils
16
17
18|l9|»
i r rr
'1
1
??
1
?3
3
INS
24
T
Comm. Insl.
10? tons
21J22J27J24
1 P [S
TITUTIONAL FUE
Resid. Oil
104 Gals.
25 26
27
7.
20
f
?9
3
L
Nat. Gas
1Q> Ft3
30|31
Residential
10? Ions
25|2G
1 1
5
28
29
30
Lf:
32
3
33
O
Wood
10?!ons
'"34
35
Anlh. Coal
10 1 Ions
3§j37
OPEN BURNING
Industrial
10? Ions
3.1.
32
33
34
•
35
36
38
39
40
41
Bilum. Coal
10 1 tdns
42
Ccmm'l- Instill.
10? tons
37
38
39
40
41
1?
43
44
45
46
47
Coke
10 1 ions
48
49
GAS
Li(ht Vehicle
101 Gals.
43
44
45
46
47
48
49
50
51
INDUSTRIAL FU
Disl.Oil
10* Gals.
52
»
54
OLINC FUEL
Heavy Vehicle
103 Gals.
50
51
52
53
54
55
5C
:L
.61
Resid. Oil
Ifl4 Gals.
M
5960
r |
Oil Hiway
103 Gals.
55
56
9.
57
7
50
0
59
0
61
62
Nat. Gas
10' Ft.3
63
64
'•
Heavy Vehicle
103 Gals.
60
61
62
63
64
i65|GC
j|
Wood
10? tons
67
3IESEL FU
Oil Hiway
104 Gals.
65[66|67
|2
1
6069
LJ
Pr
1
K
occ
0'
("I
ss Gas
|3
72
EL
Rail Locomotive
ID4 Gils.
68
i?
70
71
/
7?
0
73
74
75
7G
County
Population
103
73
7«
|
75
ff
7C
8
r
1
Ti
f.
•o
A
|
70
A
79
A
79
A
C
0'
c
Ql
Military
LTOCYCIO?
JO
11
12 13
AIRCRAFT
Civil
LTOCYClOl
17
C
L
19
ommercial
TOCYClfll
2ol21
117
22
23
Anlh. Coal
10 1 Ions
24
25
26
27
VESSELS
Diesel Oil
I(H Gals.
28
I1
Resid. Oil
104 Gals.
12
33
34
35
36
Gasoline
103 Gals.
37
1
38
ii
39
2
40
7
EVAPORATION
Solvent Purchased
Igns'lfr
41
42
13
1
44,
B
45
f
46
1
Gasoline Marketed
IDS Gals.
47
48
49
50
51
Limited Access Road
10* Miles
62.
S3
4!
55
56
67
MEASURED VEHICLE MILES
Rural Roads
lO4 Miles
58
59
60
61
62
PJ
Suburban Roads
I04 Miles
04
.65
66
67
68
69
Urban Roads
10* Miles
.70
7J
7J.
7J
1A
75
7J
n
O
w
7.0
A
2?
A
Dirl Roads
Traveled
103 Miles
10
II
lIM
Dirl
Air Sl/ips
LTO CYCLES
thaTO
.J_LL
21
Construction
Land Area
\V Acres
22l23
I
24
25
26
Rock Handling
& Sjorinj
W tons
27|28
I
29
30
31
FOREST FIRE
Area • Acres
32
33
34 35
36
ty
37
9-
\
38
5
s
Quanl.
ton 'acre
39
40
/
41
1
SLASH BURNII
Area • Acres
42
4344
2.
45
7
46
k
47
0
4G
Quanl.
tons acre
48
49
50
L
FROST CO
Orchard
Heateis
102
31 52
53
54
ITROL
Days
Fired
days yr
55
56
67
Structure
Fires
(f/yeat
58
1
59
*/
60
1
R1
t
COAL REFUSE BU
Si;e ol BV)k
10? yard3
6263
64
65
66
67
RNING
«/y_ear j
G8_l6?
7t
NATURAL SOURC
(tons)
^7iT72
73
74
7
75
u
v-6fl—
E
r
.S
T>
-<
7§
A
79
A
COIMENTS
1011
.14
"
15
f
16
/
17
C
18
1920
c\o
21
0
22
V
23
T
24
Y
25
26
27
28
2930
I
31 p
|
33
34
35
36
37
38
39
40
41
42
43
4445
1
46
47
48
49
SO
51
5253
I
54
55
56
57
58
59
60
61
62
63
64
C5
GJJ67
68
69[70]71
1 !
Zl
L3
74
75
76
77
S
C
•t
78
A
/9
A
A Oun. 219
a.'7 2
-------
AREA SOURCE
Input l: or in
Mnio
SI
1
,3
V
c
itc
10
2
IP.
10
f
LT
— ™1
10
JIC
J
cai
1
Oil)
U
h
10
5
it
i
i11
L.
iihi
oc
0
11
County AQCR
3.1 4 Pi 1.1- .7.M.9.
Pailiculale
12(13 ii^Sc
1
Anlh. r
1 Ions 1(
12li¥l4 15 16
±r ~ ~
17
itu
)> 1
17
10
EMISSION ESTIMATES HO2
>°2 N0»
,9|7
COHAIE
mn
ons
J^UJ_19 f
ON SITE IHCIHERATION
•sidrntial laduslnil
D' Ions 102 Ions
|l2|l3Tl4|lG 16
I 1 I
17
18
AIRCRAFT
Jiy Civil
1C 10? LTOCYC 10'
i2Ji3 14 15. 16
Diil Roads
Traveled
103 Miles
12|l3|l4 15jl6
lL_T_
.L7.|lO
19|z(
I
Con
LT(
J9 I
D 21 22
RCIAL A
Uiil.f
104G^
3 21J22"
"IT
t
NO
)il
Is.
23
fe
INS
24
Comm. Inst.
102 Ions
i i—
) 21 22 23
\z
(o
mcicial
KYClQl
olll 22
23
*?
ffl
An
1
24
25
H
TIT
25
26
lonsi
HC
27J2s!29!30
2W
UTIONAL FUEL
Resid. Oil N
ID4 Gals. 1
26J27
20
2? .30
Residential
ID2 Ions
25
26
!27
LJJJ
Ih. Coal
1)1 Ions
li
26
Dirt Construction
Air Skips Land Area
LTO CYCLES O3 Acres
17)18
COnMEHTS
LO]
11 12 13 14 15 16
17
C
,8
0
EPA OuR- 219
3/72
!|9 20
I
ig|2(
uk
21 22
)]21 22
Try
23
23
li
25
24
26
25 26
27
»
29 30
Diesel Or
104 Gals.
1?
2130
Rock llandlin
& SJorinf
103 tons
271
27
28
29 3C\
2^29 30
1
CO
31 32 33|34J35
_rl
al. Gas
07Ft3
11 .1? 3:
Wood
102lons
3435
SULFUR
Anth. Bit
Coal Co
36
B7 3BJ
CO
jrn.
al
39
NTE
Di
0
40
NT
St.
1
41
,
Anlh. Coal
10 1 tons
36
OPEN BURNING
Industrial
102 Ions
31 32 33
34 35
36
VESSELS
1 Resid. Oil
104 Gals.
313233
3J35
31
37 38
39
40
41
C.
Resid
Oil
4 2 [43
1
42
Ccmm'l- Instill.
)02 Ions
37 38
1?
Gasoline
103 Gals.
37 301
FOREST FIRE
!
Area • Acres
31 32 33
•
31 :2 33
34 35,
36
37 38
2. ~i
34 35
36
3738
40
3?j40
41
.12
ASHC
Anlh
Coal
44JJ5
ONTENT IM
Qitum.
Coal
46
47|48 49
,
Anlh.
10 'ions
"~i !'"
isasLS
Bitum. Coal Coke
10 1 tens 10 ' tons
«
44
45
46
47 48 49^50
i
GAS
Light Vehicle
101 Gals.
«
44
45
46_
EVAPOR
Solvent Purchased
tons yr
41
S
Quant.
ton 'acre
39
39
40
1
40
41
|
42
«
I1
f
46
2.
47 48 49
5.1
53
Name ol Per
Completing
Bilumin.
ID1 Ions
54
55 56 57
ion
rorrn
RE
Oisl. 0
104Ga
58 59 60
5
INDUSTRIAL FUEL
Oisl. Oil fte.sid. Oil
5?
„
«
OLINE FUEL
Heavy Vehicle
103 Gals.
50
51
UION
Gasoline Maideled
IflSCals.
.474819
50
SLASH BURNING
Quant.
Area • Acres Ions acre
42
41
42
43
44
43
44
45
45
46
47 48 49
50
46
47 48 49
50
5J
52
53
54
55 5C 57j58|5_9[60
j-hr
6]
SIO
il
1.
^
EN
63
MAI
"1
64
.FUEL
Resid. Oil
10* Gal.
65
66
Nat Gas
107 Fl.3
62
63
64
i
Oil Hiway Heavy Vehicle
103 Gals. 10J Gals.
555657
Limited Access Road
104 Miles
B2
53
FROST
Orchard
Healers
102
il"l
51
52
5?
S3
53
1 1
54
CO
54
55 5617
OROL
Days
Fired
days yr
55 56 57
58 59 60
6J
6?|63
MEASURED
Rural Roads
104 M les
§8 §9 gO
Structure
Fires
«/»eat
58 59J60
1 7|Z~
54
55 56 57
5859601
61
fi1
ft
61
62
63
64
3 >f
)IES
Oil
104
.15
67
68
Woe
1021
360
"1
ELFU
Hiway
Gals.
16J6?
Nat. Gas
107 U.3
09(7
)
d
ons
69 )
071
7?
Process Gas
10' II3
oPM
U
EL
Rail Locomotive
104 Gils.
68
697
VEHICLE MILES
Suburban Roads
104 Miles
64
65
CO
67
COAL REFUSE DL
SiJe olOvik
102jard3
62
62
63
64
63
6J
65
65
66
G6
67
67
68
RN
«,
68l
...
6?7
NG
year
697
68
69 7
|
07J.
12
7.3
Vcod
10? Ions
TjjbsbelH
,J
L_L
7_".J7G|7(
County
Population
103
73
74
70 7(
1 8
Urban Roads
1Q4 Miles
07J
12.
23
H
Z5Z.C
1
1"
S
I
Ti
Tl
NATURAL SOURC
(tons)
C 71
fiJ2i
72
12
73
74
1
7J
74
75 h
O 7.
75 7(
, 77
-0
, 77
f:
o
•it
78
jj
e;
••»
A
c
TJ
A
c
0
Zi
2D
A
E
c:
o
u
78
A
P
78
A
79
.A
7.3
A
Z?
A
.1?
A
A
A
-------
AREA SOURCE
Input Form
Dole
Slate
Tjl
31.
County
jUPpCc
.QilLyo
AQCR_
Name of Pcison
Completing Form
Year
of
iecoid
10] 11
TJg"
Particulale
r ~T~T — i
12 13 14 15.16
_LL Jl
EMISSION
S02
1 1 T
17)10 19|20
1
I
21
ESTIMATES 1
NO,
22
23
24125
...I/.
O2 tonsi
HC
26J27|28| 29!30
1 Itleb
31
32
CO
33
34J35
i
S
An
Co
36
,,— '
JLF
Ih.
al
37
"URCO
Cilum.
Coal
38 J39
1
NTENT
Disl.
Oil
[
(M
Resid
Oil
42 [43
1
AS
1
44
HCON
Inth.
;:oai
15 U
i
KNT (M
Dilum.
Coal
47
48
— i
49
Anth.
10* ton!
50J5li52J53
M
Bilumin.
101 Ions
54
55
56
57
5£
RESIOEN1
Disl. Oil
104 Gal.
59
60
61
62
63
flAL FUEL
Resid. Oil
104Cal.
Gales
66
67
68
N
1
•sjzo
Nat. Gas
107 II.3
"I~T~T~"
dZl l?lL3 1
±ILJ_.
flood
757677
IB
M..A
Anlh.
Ifll Ions
ioln
10
12
13
14
COW
Oilumin.
10 ' Ions
15
ON SITI
Residential
10 ' Ions
11
12
13
14
15
16
17
1o|l9
ERflAL AND
Disl. Oil
104 Gals.
20
: INCINERATION
Industrial
ID2 Ions
16
17
18
19
20
21
22
23
INS
24
Comm. Inst.
102 tons
21J22
1
a
24
TITUTIONAL FUE
Resid. Oil
104Cals.
25
26
27
2B
29
.
Nat. Gas
107 Ft3
30(31
Residential
10? tons
th
28
29
3Q.
32
.!?
Wood
34
35
Anlh. Coal
10 > Ions
36
OPEN BURNING
Industrial
102 tons
3.1
32
33
34
35
i
36
37
38
39
40
41
Bilum. Coal
10 1 tens
42
Ccmm'l • Instill.
!02 tons
37
38
39
40
41
42
43
44
45
46
47
Coke
10 1 tons
48
49J50
I
GAS
Lijhl Vehicle
10-1 Gals.
43
44
45.
46
47
48
49
51
INDUSTRIAL FU
Disl. Oil
lOUals.
52
„
OLINC FUEL
Heavy Vchicl<
103 Gals.
50
51
52
53
54
54
55
5C
:L
Resid. Oil
104 Gals.
57J S8[ 59
1 1 '
Oil Hiway
103 Gals.
55
56
57
58
59
6_0
6.1
02
Nat. Gas
107 Ft.3
63
64
•'
Heavy Vehicle
103 Gals.
60
61
62
63
6 tons
24
25
26
27
VESSELS
Diesel Oil
10* Gals
28
29
30
31
Resid. Oil
10< Gals.
I32
33
3^
35
36
Gasoline
103 Gals.
3?
38
39|40
I
EVAPORATION
Solvent FWh,ised
tons yr
41
42
43
^
44
3
45
f)
46
4
Gasoline Marketed
105 Gals.
47
48
49
50
?1
MEASURED VEHICLE MILES
Limited Access Road
10 < Miles
52
53
64
55
56
57
Rural Roads
10* Miles
58
59
60
61
6?
63
Suburban Roads
104 Miles
64
65
66
67
68
69
Urban Roads
104 M
70
71
72
73
Ics
fa
75
?c
7V
K
Cl
73
•4
78
A
7?
A
C
f"
4
10
11
DiM Roads
Traveled
JO3 Miles^
12ll3ll4
15 16
Did
AirSUips
LTO CYCLES
17)18
1
19
20
21
Construction
Land Area
Iff Acres
22
23
24
25
26
Rock Handling
& Storing
103 tons
27
28
29
30
31
FOREST FIRES
Area • Acres
32
33
34
35,
36
^
37
1
38
B
Quant.
lon'acie
39
40
|
41
|
SLASH BURNING
Area • Acres
42
43
I
44
to
45
B
46
o
47
3
Quant.
Ions acre
48
49
50
I
FROST CONTROL
Orchard
Healeis
102
51
52
53
54
Days
Fired
days yr
55
56
57
Structure
Fires
58
\
59
I
60
I
RI
z.
COAL REFUSE BURNING
Size ol BaM
10' yard3
62J63
|
64
65
66
67
«/year
68
69
7C
JATURAL SOURCE
(tons)
71
72
73
/
74
S
75
/
76
S
77
3
r
78
A
73
A
COW.1EHTS
14
/
15
V
16
&
17
T
18
0
19
n
20
21
C
22
0
23
U
24
V
25
T
26
y
27
28
29
30
31J:2
|
33
34
35
36
37
38
39
40
41
42
43
44~]45
j
46
47
48
49
50
51
52
S3
54
55
56
57
58
59
60
61
62
63
64
65
66
67
68
egbo^i
1 1
72
73
74
75
76
77
g
e
70
A
79
A
Ul
EPA 'OUR. 219
V72
-------
Slale Counly
Year
ot
iecoiil Particulale
1o|ll 1?.|l3|u'l5
ilsmr
Anlh.
IB' tons
1plljljl2 13 14 IE
ON SIT
Residential
10 ' Ions
loTil 12 13[l4[i!
1 1 1
A
Military
LTOCYC 10? LTO
lolu|l2 13 14 15
Jit
Dirt Roads
Traveled
10J Miles
10 11 i2 nfi4 15
... .. _.l.
COMMENTS
10J11 12J13J14 IS
AQCR
I. 0 1.9.
EMISSION ESTIMATES HO2 tonst
502 NO, HC
!lG 17 1flTl3 2
J It"
COf,V,U
Oiluinin.
10 ' Ions
JlBJ17|lufl9 ?
1 T IT"
E INCINERATIOI
Industrial
ID2 tons
. leliTJiBligb
1 1 1 1
OJ21 22|_23|24
.Rf IAL AND INS
Oisl. Oil
104 Gals.
o)21J22|23|24
ii rr
<
Comm. Insl.
I02 tons
0 21J22
(23 U
IRCRAFT
;ivil Commercial An
CYClOl LTOCYClOi 1
|lG l_7 JO 19 2
ol2J.22
2J2JJ
25 26l27J28l29l30 31
z'~HT£iTn
CO
32 33[34
fITUTIONAL FUEL
Resid. Oil Nal. Gas
I04 Gals. 10' Fl3
.25 26 27 20 23 30J31
L__ 1
C
Residential
I02 Ions
Mbebbs 2930 31
±11 ••••"• '
VE
Ih. Coal Diesel Oil
0' tons 10* Gals.
25 26 27 28 29 301 31
Dirt Conslruclion Rock Handling
AirSI/ips Land Area & SJoiing
LTO CYCLES 10" Acres I03 Ions
16 .7-104,912
3J21 22
Mil
16 17 18 19J2
c ~6 u\i
EPA Dun. 219
V72
021 22
TY
2324
23 24
25 26 27 28 29 30 31
•
25 26 27 28T2"9l30 3p
TT~
3? ?;
PA
Wood
102lons
.34
35
SULFUR
Anth. Bit
Coal Co
36
17
38|
CO
jm.
al
39
NTE
Di
0
•
Anth. Coal
10 1 tons
36|37
PEN BURNING
Industrial
102 tons
32 33
^
W36
~
i
SSELS
Resid. Oil
104Gals.
12.33
34
Area
32 33
:233
34
34
35
36
38
39
4_0
NT
St.
1
i!
41
(M ASH CONTENT (M
Resid Anth. Bitum.
Oil Coal Coal
42 [43 44 15
_T~"^
46 47
i
Bitum. Coal
ID1 lens
42 43J44 45
46J47
48J49
Anth.
101 Ions
~§TT
Coke
10 1 Ions
48 49J50 51
GAS
Ccmn'l- Instill. Light Vehicle
102 Ions 101 Gals.
37
38
33
40
Gasoline
103 Gals.
32
38
FOREST FIRE
• Acres
35
36
4
35
36
37
$
37
38
2.
38
39
40
i1
42 43 44 45
46 47
48 49
Name ol Per
Completing
Bitumin.
10 1 Ions
54
55
INDUSTRIAL
Disl. Oil
I04 Gals.
5?
53
OLINC FUEL
Heavy Vchicl
103 Gals.
50 5J
EVAPORATION
Solvent Purchased Gasoline Marketed
tons yr 10$ Gals.
41
S
Quant.
ton 'acre
39
3?
40
|
40
41
I
42 4j 44 45
2- 2. ^
46 42
/
SLASH BURNII
Are) • Acres
42 43 44 45
il
42 43 44J45
. ^-
46 47
4849
GO 61
52
53
54
i
54
55
55
IP.
FUI
5C
17
ton
Form _
K 59
A11EA
Input
RESIDEN
Oisl. Oil
I04 Gal.
60
61J62|G3
:L.
Resid. Oil
. IflUals.
5?l58l5.?
i •
Otl Hiway
I03 Gals.
56
57
Limited Access Road
104 Miles
52
5j
«£
70
r
o
!**
70
A
c
o
f;
•A
A
n
o
»<
29
A
:E
cr
Ci
~>ti
A
c
o
C
78
A
7!)
79
A
A
7?
J\
73
A
A
-------
AREA SOURCE
Input Form
Onic
Stale
Li:u
Year
ol
fecord
loin
County
Tlijjlfi
.QhltlQ.
AQCR
olliS
*m
Name of Person
Completing Form
Parliculale
zlnfiTTs'ie
EMISSION ESTIMATES HO2 tonsi
S02
._——
rjUem
20 21
NO,
22|i3.|24J25
HC
CO
31)32
1
33
34
35
SULFUR CONTE NT ('.)
Anlh.
Coal
36
___j
17
Bilum.
Coal
38J39
1
Hist.
Oil
40 41
Resid.
Oil
42143
1
ASH CONTENT |M
Anlh.
Coal
44J.«5l46
1 1
Oilum.
Coal
47
48
49
Anlh.
101 Ions
50!5H52l53
1 \3
Bilumin.
10' tons
54
55
56
57
58
RESIDENTIAL FUEL
Oisl. Oil
104 Gal.
59
60
61
3
62
5
63
5
Resid. Oil
104Gal.
G4J65
66
67
a
i
Nat. Gas
10? II. J
69
70
71R2J73
I nM3
flood .
102 Ions '•.
7J
75176
77
£
78
Anlh.
101 tons
10J11
1
i
12
13
I?
COW
Bilumin.
10l Ions
15
Oil SIT
Residential
10 1 Ions
10J11
I
"2
i
li
17
ia[l9
i
1ERC IAL AND INS
Oisl. Oil
104 Gals.
20
• INCINERATION
Industrial
102 Ions
J6
17
18
»
»
y
22
"J
23
5
Comm. Ins
102 tons
21
a
23
Z
24
5
.
24
>
TITUT10NAL FUE
Resid. Oil
104 Gals.
25
26
77
1
7U
5
23
7
L
Nat. Gas
107 Ft3
30|31 32
Residential
102 tons
^
5
"1
2J
M
3.Q
l_5
33
7
Wood
il02tons
^l
35
Anlh. Coal
10 1 tons
36|37
1
OPEN BURNING
Industrial
102 Ions
31 32
1
33
34
— 1
35
36
38
39
40
41
Bitum. Coal
10 ' tons
42
Comm'l- Instill.
ID2 Ions
37
38
39
40
41
42
43
44
45
46
47
Coke
10 1 Ions
48
49
SO
i
GAS
Light Vehicle
103 Gals.
431
44
45
«
47
48
49
51
INDUSTRIAL FU
Oisl. Oil
)04 Gait.
52
53 54
OLINC FUEL
Heavy Vchicli
103 Gals.
5?
51
52
53
54
55
3
56
*/
:L
57
Resid. Oil
104 Gals.
r58
59J60
!
OH Hiway
103 Gals.
55
56
52
58
T
59
61
62
Nat. Gas
10' Ft.3
63
64
•'
Heavy Vehicle
103 Gals.
60
61
6?
63
64
H
Wood
102 Ions
6J
JIESEL FU
Oil Hiway
104 Gals.
65J66
67
1 \s
ca
69
Process Gas
10' II3
70
71
72
£L
Rail Locomotive
104 Gals.
68
69
70
71
7?
7
73
7-1
75
70.
County
Population
103
73
74
75
7
7C
2.
Z?
r/
c
! *-»
IB
A
.1
tt
70
A
79
A
79
A
filililary
LTD CYC 10?
loiiiiuru
jJik
AIRCRAFT
Civil
LTD CYC 10'
11
1.5
icluiio
olelr
Commercial
LTOCYClfll
19
20)21
|
22
23
Anlh. Coal
10 1 Ions
24
15
26
27
V£
Diesel Oil
10* Gals.
28
29
30131
«h
SSELS
Resid. Oil
, 104 Gals.
^
33
3"
V
35
a
36
1
Gasoline
)03 Gals.
37
2
38
O
39
°\
40
^
EVAPOR
Solvent Purchased
tons yr
41
42
43
44
ti
45
|
«
tnoN
Gasoline Marketed
10$ Gals.
11
40
41
50
5J.
Limited Access Road
10< Miles
52
53
54
55
56
57
MEASURED \
Rural Roads
104 Miles
58
.59
60
.61
62
63
/EHICLE MILES
Suburban Roads
104 Miles
.6J
65
M
6?
68
C9
Urban Roads
104 Miles
IS.
11
7^
7J
74
Z§
Zfi
n
c
o
u
2Q
A
79
A
DiM Roads
luveled
10J Miles
10
11
r12ll3[l4
1 !
15
16
Di'l
Air Stfips
LTO CYCLES
Ii7
18
19
20
21
Construction
Land Aiea
10" Acies
22
23
24
25
26
Rock Handling
& SJoiing
103 Ions
27)28
1
29
30
31
FOREST FIRES
Area • Acies
32
33
34
35
36
*/
37
0
38
0
Quant.
ton 'acre
39
40
/
41
|
SLASH BURNING
Area • Acies
42
43
44
|
45
1
46
tf
47
7
Quant.
tons acre
48
49
50
|
FROST
Orchard
Heaters
Ifl2
J1
62
S3
CONTROL
54
Days
Fifed
days yr
55
56
67
Structure
Fires
«/yeai
58
59
|
60
7
fil
7
COAL REFUSE BURNING
Slie ol B^ik
10'yard3
62
63
64
65
6G
67
«/year
68
69
70
NATURAL SOURCE
(tons)
71
72
73
74
3
75
£
76
M
77
CT
U
<
78
A
79
A
COWAENTS
10J1l|i2ll3Ti4
f*1 1 ^ 1 0 1 C \
*~~ 1/1 If 1^1
15
A»
16
A
17
y
18
19|20J21
C |O|V
22
^
23
r
24
r
25
26
27
28
29J30
|
31 b
1
33
34
35
36
37
38
39
40
41
42
43
44
45
46
47
48
49
50
51
52
53
54
55
56
57
58
59
60
61
62
63
64
65
66
67
68
eglyo'fyi
1 |
72
73
74
75
76
77
g
S
70
A
/9
A
EPA DuR< 219
3/7 J
-------
AfiEA SOURCE
Input form
Dale
Name ol Person
Compiling Foim
CO
31
32
33
34
35
SULFUR CONTENT ('.)
Anlh,
Coal
36
»7
Dilum.
Coal
38
39
Disl.
Oil
40 L
1
Resid
Oil
42
J
43
ASH CONTENT Ft3
30)31
....
Residential
10? Ions
*
«
"1
21
29
30.
i —
1?
H
V
Wood
102lons
34J35
1
Anth. Coal
10 1 Ions
36|37
1
OPEN BURKING
Industrial
10? tons
3.1
3J
13
34
i
35
36
30
IS
40
41
Bilum. Coal
10 1 lens
47
Ccmm'l- Instill.
10? tons
37
38
39
40
41
42
43
44
45
46
47
Coke
10 1 ions
48
49
50
1
GAS
Lijlit Vehicle
103 Gals.
43
44
45
46
47
48
49
51
INDUSTRIAL FU
Oisl. Oil
10* Gals.
52J53
54
7
OLINC FUEL
Heavy Vehicle
103 Gals.
50
51
52
53
54
55
JJ
SG
5
:L
Res
57T58
id. Oil
Gals.
59| GO 61
"T%aT
Oil Hi way
103 Gals.
55
56
"Z
57
Z
58
3
59
3
Nal. Gas
10' Fl.3
62 63
64
I
Heavy Vehicle
103 Gals.
Ill
60J.6J |62|63
6?
65
4
GC
2.
Wood
10? Ions
67
)IESEL FU
Oil Iliway
104 CaH.
65
66
3
67
£
GO
69
Process Gas
lO'll3
— 1 1 1
1
EL
Rail Locomotive
10* Gals.
68
§?
70
11
7?
T
7-1
7!>
76
County
Population
103
73
74
/
75
3
7G
"£-
77
S
I'l
C,
O
78
A
g
C
70
A
79
A
L?
A
no CYC 10?
10 11 12 13
AIRCRAFT
Civil
LTOCYC 10 1
zefffflit
Commercial
LTD CYC 10 1
19
"IT
If2
23
1
Anlh. Coal
10> tons
.?J 25
26
27
VE
Diesel Oil
104 Gals.
28
29
30131
SSELS
Resid. Oil
104 Gals.
1?
3?
/
34
i|
3$
5
36
(3
Gasoline
103 Gals.
32
39J40
~]\S
EVAPOR
Solvent Purchased
Ions yi
-------
AREA SOURCE
Input Form
Dale
Stale County
AQCR
Name ol Person
Completing Form
Year
ol
fecord
^
Paiticulale
17.
16
"1—
S02
NO
r£S(102tonsi
4|2S
W
HC
26J27
•^-H
1 —
H1
6
30
I
CO
31
32
33
34135
I
SULFUR CONTENT (M
Anlh.
Coal
36
37
Bitun.
Coal
38
— J
39
Disl.
Oil
4o|41
1
Resid
Oil
42 [43
I
ASH CONTENT |M
Anlh.
Coal
44 MS
J
46
Dilum.
Coal
47
48
49
Anlh.
10* tons
50'51I52
1
53
Bitumin.
1C1 tons
54
55
56
57
58
RESIDENTIAL FUEL
Oisl. Oil
104 Gal.
*
60
61
6_2
63
Resid. Oil
' 10* Ol.
64]65
1
66
67
!>§
i
Nal. Gas
Ifl7 II. J
69
ZP.
Z1
7273
1
Wood .
102 Ions .
74
757677
1 I'
I
II
•a
I&I.A
Anlh.
10 1 Ions
1ohl 12J13
Residcnti
10 ' Ions
lol 1l|l2ll3
TTT
1 Ions
15
SIT
15
-
16
17
iali9
: IIICINER
Indusli
102 loi
16
17
18
\TIC
al
s
"I
ERflAL AND
Disl. Oil
104 Gals.
20
)N
20
_21
Co
1C
2i|
2?
23
INS
?i
mm. Ins).
2 Ions
22
^)
23
"R
24
b
TITUTIONAL FUE
Resid. Oil
104 Gals.
25
26
27
28
29
L
Nal.
I07
3P
Residential
]02 Ions
tM
28 [29 130
TT
31
Gas
32
33
Wood
102lons
1335
1
Anlh. Coal
10 > Ions
36[37
OPEN BURNING
Indusliial
102 Ions
3.1
— i
32
33
3435
i
36
38
39
40
41
Bilum. Coal
10 1 (cms
42
Ccmm'l- Instill.
102 Ions
37
38
39
40
41
42
1
43
44
45
"6.
47
Coke
10 1 Ions
48
49
50
1
GAS
Li{ht Vehicle
lip Gals.
13.
44
45
46
47
48
49
51
INDUSTRIAL FU
Disl. Oil
104 Gals.
52
53
54
OLINC FUEL
Heavy Vehicle
103 Gals.
50
51
52
53
54
55
5C
:L
Resid. Oil
104 Gals.
57[58|59l60[61
! 1
Oil Hiway
103 Gals.
55
56
5Z
58
59
62
Nal. Gas
10' Ft.3
G3
64
•'
Heavy Vehicle
103 Gals.
60
61
62
63
64
65 6t
1
Wood
102 Ions
67
)IESEL FU
Oil Kiway
10< Cals.
i
T
67
CI/69
Process Gas
lo'n3
70
71
12
EL
Rail Locomotive
104 Gals.
68
1
70
71 7?
I
23
24.
25
IP
County
Population
103
73
74
T
75
"i
7C
8
2?
a
77
o
JQ
A
s
ig
70
A
2.9
A
79
A
Military
LTD CYC 10?
10
11
12
13
AIRCRAFT
Civil
LTOCYC10'
14
15
1C
17
IB
Commercial
LTOCYClfll
19
2ol21
22
23
Anlh. Coal
10> tons
24
15
26
27
VE
Diesel Oil
.JO4 Gals.
28
29
30
31
SJELS
Resid. Oil
, 104 Gals.
32
33
34
35
36
Gasoline
1Q3 Gals.
3?
3.0
39
40
EVAPOR
Solvent Birchiised
tons yt
41
42
43
1
44
«
45
5
46
3
i DON
Gasoline Marketed
IQSGals.
47
48
49
50
il
Limited Access Road
1Q4 Miles
52
52
54
55
56
57
MEASURED
Rural Roads
104 Miles
58
5J
60
61
62
63
/EIIICLE MILES
Suburban Roads
10* Miles
6J
15
16
67
6869
1
Urban Roads
104 Miles
70
Zl
13,
7J
14
25
IE
22
c
_0
u
*t
ID
A
29
A
Dirt Roads
Traveled
103 Miles
10 11 12 13 14 15 16
Did
Airstrips
LTO CYCLES
17llT[l¥l20
1 1 1
21
Construction
Ljnd Area
103 Acres
22
23
24
25
26
Rock Handling
& Morinj
103 tons
27
28
29
30
31
FOREST FIRES
Area • Acres
32
33
34
35,
36
37
38
Quant.
Ion 'acre
39
40
41
SLASH BURNING
Area • Acres
42
43
44
45
46
47
Quant.
tons acre
48
49
50
FROST CONTROL
Orchard
Heaters
'A
52
S3
54
Days
Fired
days yr
55
56
57
Structure
Fires
«/ ear
50
5"
59
O
60
O
fi1
|
COAL REFUSE BURNING 1
Size ol Bvk
10'yard3
62
63
64
65
66
67
n/year
68
69
7C
NATURAL SOURCE
(tons)
71
72
73
74
|
75
3
7677
ok
r
'•3
o
•4
78
A
73
A
COdWENTS
10J11
*|s
12
5
13
F
14
*
15
16
C
17
6
18
U
19
/u
20
T
21
y
22
23
24
25
26
27
28
2930
I
T
33
34
35
3§
37
38
39
40
41
42
43
44|45
I
46
47
48
49
SO
51
52
53
54
55
56
57
58
59
60
61
62
63
64
65
66
67
68
69|70|71
I I
72
73
74
75
LQ
77
S
S
70
A
79
A
EPA Dun- 219
3/72
-------
SDIc
1 2
31
Year
ol
iecord
10J11
•7\5
Coun
'3Ji •
:ib"
ly _
^ -/)
Pailiculale
Anlh.
I01 Ions
UlITl
— 1__
1
«|.\
Mid
LIOC
10 U
Jl?|'JJ
I 1
0
10 ' Ions
'I12)!3]1
1 1 1
lafy
•YC 10?
12.1J1 1
5
1 15
(SIT
4M5
Al
C
LIOC
1
7
'IL
I6
\OC(?
n
(II
9,
.t
[MISSION
8p9
cow
Dilumin
IO1 Ions
J6
17 J
OJJ 9
1
20)21
ESTIM
N
22(23
lERflAL AND
Disl. Oil
IO4 Gals.
20 2J
22J23
ATE
3,
b
INS
24
: IHCINERATION
Indusliul Comm. Inst.
13? Ions 10? Ions
16
171
RCRAFT
ivil
:YCIO'
i£
Di'l Roads
Traveled
103 Miles
10111
12 13 1
J-JLLL
415
16
L"J
Ai
LTO
1~
17 ]l
8 1£PO 2_1
C
L
8 13
2223
....
ommcicial
TO CYC 10 1
2ol2il22[23
"rrr
Dirt
r si/ips
CYCLES
f|lJl2021
COriMEHTS
vol 1 1
(>[ i_
12 I? 1
0\V c
4 15
- f
EPA QuR' 219
V72
16
S
17 1
f I
8 19
?K"
20 21
C.
An
1
Si
25
zy
TIT
25
0?
26
"~1
UT
Re
10
26
lonsi
HC CO
27J28|29[30 Sl^bsMsS
1 |5" [0 III
ONAL FUEL
sid. Oil Nat. Gas Wood
1 Gals. 107 Ft3 10?lons
27 .20 23 apjjti 32 3_j 34J 35
SULFUR
Anlh. Oil
Coal Co
36 J7 38J
_, _J
CO
urn.
at
39
YTENTC. ASHC
Disl. Resid Anlh
Oil Oil Coal
24
24
/LI
25
25
r
26
27.J28 29J30 31J32 33 34J35
36 37 38
39
40 41
42 43 44 45
46
VESSELS EVAPOR
1 Diesel Oil Resid. Oil Gasoline Solvent fr'ch.ised
104 Gals. io4 Gals. IO3 Cats. Ions yr
27 28 29 30131 32 33 3J 3S_
35.3731
FOREST FIRE
Rock Handling
& Sjoring
IO3 Ions Area • Acres
27 20 29 30 31 32 33 34 35
36 37 38
2 1 J
•
26
}^
27 28 29 30 31 C2 33 34 35
36 37381
39J40 41
S
Quant.
Ion 'acre
39
4041
I /
42 43 44 45
~irr
46
a
47J48 49
"t"~
Name ol Per
Completing
Bitumin.
IO1 Ions
4 K
INDUSTRIAL
Disl. Oil
IflUalS.
5?
T
OLINC FUEL
Heayy Vehicle
IO1 Gals.
5051
moN
Gasoline Marketed
105 Gals.
12
SLASH 8URNI
Area • Acres
42 43 44 45
39
4041
42 43 44|45
. _=«
46
47
|
46
47
4J[49
50 51
52,
535,
B
455
5657
ton
Form
58 5_9
RESIOEN1
Oisl. Oil
IO4 Gal.
60 G 1
FUEL
Resid. Oil
IO4 Gals.
15G 57[5j]59
1
Oil Hiway
IO3 Gals.
5657
Limited Access Road
IO4 Miles
52
53 S
d Proce
tons I 10' I
J 69 70[7 11
ail iDcomoli
IO4 Gils.
!J6? 70J71 !
3
s C
.3
72
"
it
I?
7J
las
13
Wcod
10? lens .
7j
74
«
7G7op7
County o
Population S
IO3 &
73
74
T
75 7C Ti
W\0 "
s Uiban Roads
10^ Miles
3 69 7o|7J
_ L
72
73
74
75 ?G 7V
)|NG NATURAL SOURC
(tons)
a 69 7C 71
l|69|7ol71
1 1 1
72
21
7JH74
Hal
!75 76 77
oT3
7?
74
75 76 77
C
o
T»
-a'
7J
r:
o
.75
A
c
o
•5
78
A
O
70
A
:E
c:
o
Ti
A
g
C
78
A
1
7?
A
A
79
A
/9
A
c
(U
c
B
t
0.
C
p.'
4
c
m
C'
8E
t
-------
AREA SOURCE
Input l:oim
Dole
County
igcn
Name of Person
Complelinj Form
Year
ol
tecoid
ipjjl
5i£
Parliculale
CMissior
S02
ITTlB
r
19)20
1
u
ESTIMATES (
NO,
22[23l24l25
1 1 !/
O2 lonsi
HC
2el27 23)29(30
ztr
J2[69
31
32
CO
33
34J35
1
S
An
Co
36
., '
JLf
Ih.
al
37
URCO
Bitum.
Coal
38
-J
39
NTENT
Dist.
Oil
40^1
f
(M
Resid
Oil
42)43
1
ASH CON
Anlh.
Coal
4JJ.|5]46
n_l_
'ENT (M
Bilum.
Coal
47
48
,
49
Anlh
Ifl'.K
50151
ns
52|53
1
Bilumin.
ID1 Ions
54
55
56
57
50
RESIDEN
Dist. Oil
ID4 Gal.
59
60
61
62
63
IAL FUEL
Resid. Oil
• 10* Gal.
64
65
66
67
S§
Nat. Gas
Ifl7 11.3
69
7071
1
7273
1
Wood . {
10* Ions ".
74) 75 ?6:| 77
"TTt
COMMERf IAL AND
Anlh.
Ifll Ions
lOllI 12 13 11
1
Bilumin.
1 10 1 Ions
IS
Ifi
17
liBlia
INSTITUTIONAL FUEL
Oisl.Oil
104 Gals.
TO1
'1
7?
73
74
Oil SITE INCINERATION
Residential
to' Ions
10mll2m[l4rJ5
I I n r
Indusliial
I32 tons
16
17
18
19
20
Comm.
Inst.
102 Ions
21
22
23
24
(|o|l
Resid.
Oil
104 Gals.
75
?6
77
71)
73
Nal. Gas
107 Fl3
30[31
"
32
3:
Wood
102lons
34
35
( INDUSTRIAL FUEL
Anlh. Coal
10 1 tons
36
— H
37
38
39
40
41
Bilum. Coal
10 1 lens
42
OPEN BURNING
Residential
102 tons
25|26
27|
28
1 1 1
29
30
Induslria
102 Ions
31
32
33
34
35
,.
i
36
Ccmm'l- Instill.
102 tons
37
38
39
40
41
42
43
44
45
46
47
Coke
10 1 Ions
48
49150
i
i
51
Dist. Oil
104 Gals.
52153
54
55
5C
Res
104
•
d. Oil
Gals.
57J58159J60
GASOLINE FUEL
Li(hl Vehicle
101 Gals.
43
44
45
46
47
48
49
Heavy Vehicle
103 Gals.
50
51
52
53
54
r
, ,«
Oil Hiway
103 Gals.
55
56
57
58
59
61
6?.
Nal. Gas
107 FI.3
63
64
65
GC
Wood Process Gas
10? Ions
67
6.069
1
70
O'l|3
71
72
DIESEL FUEL
Heavy Vehicle
103 Gals.
60
61
62
63
64
OH Hiway
!04Gals.
.
67
Rail Locomotive
68
104 Gals.
69
70
71
7?
73
74
75
70
County
Population
103
73
74
6
75
O
7C
T
77
t>
1 \j
i **
78
A
79
A
r
IL
fe
•a.
70
A
79
A
AIRCRAFT
Military
LTD CYC ID2
10
11
12
13
Civil
LTD CYC 10'
14
15
1C
17
10
Commercial
LTD CYC 10'
liliohl
I I
22
23
Anlh. Coal
I0> Ions
24
25
26
27
VESSELS
Diesel Oil
JO4 Gals
28
29
30
31
Resid. Oil
ID4 Gals.
32
33
34
35
36
Gasoline
103 Gals.
37
38
39
40
EVAPORATION
Solvent Purchased
tons yr
41
42
43
I
4,4
*>
45
Z
46
7
Gasoline Marketed
10$ Gals.
V
48
4,9
50
51
MEASURED VEHICLE MILES
Limited Access Road
104 Miles
52
53
54
55
56
$7
Rural Roads
10* Miles
58
59
60
61
62
63
Suburban Roads
104 Miles
G4
65
6?
67
G8
69
Urban Roads
104 Miles
ITO
71
n
n
74
75
7e
7V
K
a
u
•4
78
A
79
A
Oirl Roads
1 raveled
103 Miles
10
11
12 13
|
14
15 16
1
Dirt
AirSI/ips
LTO CYCLES
17
18JI9
|
20
21
Construction
Land Area
V Acres
2?
23
24
25
26
Rock Handling
i SJorinf
101 tons
27
20
29
30|31
|
FOREST FIRES
Area • Acres
32
33
34
35
36
37
38
Quant.
ton 'acre
15
40
41
SLASH BURNING
Area • Acres
42
43
44
45
46
47
Quant.
Ions. 'acre
48
49
50
FROST CONTROL
Orchard
Heaters
102
J1
52
S3
54
Days
Fired
daysyr
55
56
57
Structure
Fires
«/Y«a'
58
I
59
O
60
2.
r
-------
SUIc
Year
of
(ecoid
10
11
10
—
10
11
ll
K
ITT
r~
i
ii
i
3
County
Parlicula
12
13J141
Anlh.
I Ions
i- — t — i —
12lnFl«
tsid
O1 t
1?
Military
LTD CYC
JO
n
il
I
0!l<
L'ulia!
ons
dul
1
10? LT
13. Ill
1
r, 7
SlZ
le
15.16
\QC
0
i.
IT]
R
i
10
_Ll_L
c
Oilumin
101 Ions
15 16
i
17
Itl
EMISSION ESTIMATES (10?
19|2(
|
orae
11 ?r
ITE INCINERATION
Industrial
10? Ions
IS 16
17
•
AIRCRAF
Civil
0 CYC 10
r™
•nite
Dirl Roads
Traveled
ID3 Miles
10
n
12
1
1314
^
COMMENTS
||
y\
12
A/]
V2
13 14
f&
219
15 16
1
I
LT
17]
18
T
ID
1
C
\iri
OC
18
15 16
R D
11
o
19(20
Con
LTC
) 21 22
RflAL d
Uisl.
104G.
2l] 22~
h
Comm.
10? 1
?.l|22
L
mcrcial
CYC 10
J 21 12
zfe
ND INS
Dil
Is.
r\
M
Ins
ins
£
i
i?
?4
1
1.
24
kl
An
1
25
S1
TIT
26
lonsi
HC CO
27|28! 29 30 31 32 33|3435
H-
5T3 P
UTIONAL FUEL
Resid. Oil Nat. Gas Wood
104 Gals. IOJ Fl3 I0?lons
?6
1
27J28
3
H
23 30J31 32 3j 34] 35
7 'n^Vl
SULFUR CONTENT (M ASH C
Anlh. Qiluoi. Disl. Resid Anlh
Coal Coal Oil Oil Coa
36
J7 38]39 40J41
."11
Anlh. Coal
10 1 Ions
36
OPEN BURNING
Residential • Industrial
10? Ions 10? Ions
?.5J26]27_
Ih. Coal
O' tons
15
26
ifl Construction
trips Land Area
YCLES Iff Acres
I9|20
•4 \C
21 22
21 22
0 V
23
23
Jj
24
f
25
25
y
26
26
22
28
29J30 31 32 33 34J35
r , [
36
VESSELS
Diesel Oil Resid. Oil
I04 Gals. 10.4 Gats.
3&
29 30 31 32 3J 3J 3J
36.
37 38 39 40 41
T,2-
12143 14 15
r _.
Bilum. Co
10 1 tens
42 43 44 451
ON
46
u
al
46
7-
rENT (M
Dilum.
Coal
47
47
7
*
;49
Anlh
10'lc
50:51
ns
52
I (,
Coke
10 1 Ions
48
49>50
i
GAS
Ccmm'l- Instill. Lijht Vehicle
10? tons IO-1 Gals.
37 38 39 40 41
42 43144 45
- h -1
46J47
EVAPOR
Gasoline Solvent Rircluscd
10^ Gals. tons yr
37J38 39 40 41
h 7lo
FOREST FIRES
Rock Handling
4 SJorinj Quant.
W Ions Area • Acres ton 'acre
27
27
28
28
29 30,31 32 33 34 35
36
37 38 39 4041
37 ir
42 43 44 45
1° IL
46
lo
48
49
51
53
Ic,
Name ol Person
Completing Fom
Oitumin.
10' tons
54 SsTsO 57
•X"
5E
E.
i
RE
Disl. 0
104GJ
59 60 61
1 5'
INDUSTRIAL FUEL
Disl. Oil Resid. Oil
10* Gals. . !04 Gals.
52l53
54155] 5C 5?>58|59IGOJ61
"II '-; 'T
SID
il
I.
— [
62
81
AJIEA SOUR
Input Form
Date
EH
63
ft
;IA
64
LFUEL
Resid. Oil
10* Gil.
«
66
Nal. Gas
10; Ft-3
62
OLINEFUEL
Heavy Vehicle OH Hiway Heavy Ve
103 Gals. 103 Gals. 103 Gil
50
51
UION
Gasoline Marketed
105 Gals.
47
SLASH OURNII
Area • Acres
42 43 44 45
*
[29]30 3iHr2 33 34 35
1
36
37 38 39 40 41
42 43 44 45
46
46
47
47
48
is.
50_
59 60J61
1
62
63
64
1
hide
s.
yJM
MEASURED
Rural Roads
10* Miles
58
596061
Structure
Fires
»/year
50
59 60 R1
I 6 >
i?
63
65
3
6C
1
6?
68
CE
Nat. Gas
Ifl7 It.3
i
69170 71
1
Wood
10? Ions
67
)IESEL FU
OH Hiway
10* Gals.
65
[66
7
67
5
GH69
P
To
EL
Rail loco
10* Gi
68
J
/EIIICLE MILES
Suburban Roads
I04 M les
64
65
06
67
COAL REFUSE OU
Size ol Sink
10? yard3
62
54 55 56 57
58
59 60 61
62
63
63
64
64
65
65
60
66
67
61
6D
69
RUING
68
G8
69
[69]
70
2
70
]
r
70
™
y"
2-1. /
ocess Gas
71
noli
s.
n
72
ve
T
73
flood
10? Ions .
74
74
7576
i
75
70
County
Population
10'
73
74
75
7
7
Urban Roads
10/1 Miles
71
~>l\n
74
IATURAL
(tons)
7T1
ft
72
22.
73
74
3
7J
74
75 7C
7V
'±
77
77
n
SOURC
"75
2.
75
76
T
77
5
LQ
77
tr
g
LI
7(1
r:
t*
711
A
O
s*
c:
.2
T!
78
A
E
r.
o
Ti
78
A
S
C
•J.
70
A
7S
79
A
79
A
73
A
73
A
/9
A
-------
AREA SOURCE
Input form
Dale
SDK
LTJ
County
'
AQCR
Name ol Person
Complelinj Form
Yeat
ol
\CCOIl)
10)11
7l3"
Particular
17.
13[lVl5
1 i
16
EMISSION
S02
J7[lO
19)20
I
21
ESTIMATES 1
NO,
22
23
24l25
I/
O2 tons
26)27
.JL
1
HC
28|29
Ji
30
0
31
32
CO
33
34J35
1
S
An
Co
36
JLF
Ih.
31
37
unco
Bilum.
Coal
38|39
J
NTENT
Oisl.
Oil
40 J41
I
C.)
Resid
Oil
lllil
AS
/
44_
HCON
Inlh.
[loal
•isloe
I
fENT IM
Bilum.
Coal
47
48
49
I— r-
Anth.
101 Ions
50!5li52J53
~ TT
Bitumin.
Ifll tons
54
5E
50
57
5G
RESinENl
Oisl. Oil
IB4 Gal.
.i?
6Q
6.1
62
63
FIAL FUEL
Resid. Oil
- 10* Cil.
64J65
1
66
67
68
Hi
U
69|70
1
Nat. Cis
73
I
M 67 68 6j)J™T7l]7 2J73 74J75 26J77
flood
I02lons .
10
MA
Anlh.
I0' tons
10)11
I
n<
i
iojn
|
12
sid
)' 1
s
13
i-nti
ons
*
U
COW
Bitumin.
101 Ions
15
Oil SIT
al
14
15
16
:IN
J6
_17
«
19
ERCIAL AND
Uiil. Oil
104 Gals.
20
CIIIERATION
Indusliial
ID2 Ions
17
18
»
20
21
Co
_l
21
22
23
INS
24
mm. Inst.
2 tons
22
23
H
TITUTIONAL FUE
Resid. Oil
I04 Gals.
25 26
27
28
23
L
Nat. Gas
30
Residenlial
102 Ions
t
5
28
29
30
1!
[_
I?
33
Wood
I02lons
34
35
Anlh. Coal
10 1 tons
36
OPEN BURNING
Industrial
102 Ions
31
32
33
35
......
36
37
38
1?
4_Q
41
Bilum. Coal
10 1 tens
42
Ccmrn'l- Instill.
I02 Ions
37
38
39
40
41
42
43J44
45
46
47
Coke
10 1 tons
'i?
49 50
i
GAS
Li(ht Vehicle
103 Gals.
43 44
45
46_
47
48
49
51
INDUSTRIAL FU
Disl. Oil
104 Gals.
t
54
OLINE FUEL
Heavy Vehicle
I03 Gals.
50
51
51
53
54
55
SC
:L
51
•
Resid. Oil
104 Gals.
5j|_59j60
-tr
OH Hiway
103 Gals.
55
56
57
58
59
i
61
Nat. Gas
02 63
64
•'
Heavy Vehicle
103 Gals.
60
61
6263
i n~
64
ii
61
l(
67
5IESEL FU
Oil Hiway
104Gals.
65[6GjG7
1 1
Wood
)? tons
60
i?.
Pr
1
»|
oce
0'
—
ss Gas
I3
12
EL
Rail Locomotive
104 Gals.
68
69
70
71
7?
73
Z-
7G
76
County
Population
73
71
3
75
2L
7G
6
2?
Ti
C
O
IS
A
C
O
•fi
70
A
29
A
23
A
Military
LTOCYCIO?
10
11
12
13
AIRCRAFT
Civil
LTOCYC 10'
14J15
1
.16
17
10
Commercial
LTOCYC 10 1
19
2o! 21
I
22
23
Anlh. Coal
10> tons
24
25
26
27
VE
Diesel Oil
10^ Gals.
28
29
30131
1
SSELS
Resid. Oil
10* Gals.
b
33
34
3$
36
Gasoline
103 Gals.
31
38
39
40
EVAPOR
Solvent fliich.ised
tons yt
41
42
f
44
45
46
inoN
Gasoline Marketed
105 Gals.
12
48
1?
50.
5J
Limited Access Road
10
-------
AREA SOURCE
Input form
Date
SUIc
Counly
-ij? 3.lib|.r,.
_=ii L -L 3 J.QJj£J _L
AQCIi
_
1 [i)
Name ol Person
Completing Form
Year
ol
ttcord
10J11
t5ls:
Pailiculale
12[l3lll|is!.^
EMISSION ESTIMATES HO2 tonsi
502
17 MB!
19
20
21
NO,
25
HC
23
CO
tt3
34
35
S
An
Co
36
•
JLF
th.
al
)7
URCO
Uilum.
Coal
38
'
39
NTENT
Disl.
Oil
40J41
C.)
Re
0
42
Oil
44
iH CON
P,nlh.
Coal
J5146
1.
fENT (M
Bilum.
Coal
47
48
49
Anth.
10 ' Ions
50i5lis2J53
1 t
Bitumin.
I01 tons
54
5E
565750
1 1
RESIDE!!
Disl. Oil
104 Gal.
59
60
61.
62
63
flAL FUEL
Resid. Oil
104Gal.
6«]65
66
&
68
Nal. Gas
I07 11.3
r T
1 1
1 »'cod
102lons .
Z?I?3 7_4J25JZM7J
«c
78
Anlh.
10> Ions
iljujji
13JU
T
cow
Diluinin.
10 ' Ions
15
Oil SIT
Residential
10 ' Ions
•ioini 12 m
:J tnL
15
JG
17
18
J?.
1ERCIAL AND INS
Disl. Oil
104 Gals.
20
1 INCINERATION
Industrial
13 ^ Ions
16
17
18
19 bo
1
21
i?
23J24
Comm. lust.
102 tons
21J22
23(24
h. in
TITUTIONAL FUE
Resid. Oil
104 Gals.
?f>
?fi
?7
?n
?=)
L
Nal.
107
30|31
Residential
102 Ions
25
26
i
27)
a:
29
30
Has
:|3
3?
T
Wood
102lons
34J 35
1
Anlh. Coal
10 1 Ions
36
OPEN BURNING
Industrial
102 Ions
3.1
32
33
3435
1
i
36
37
38
39
40
41
Bitum. Coal
ID1 Ions
42
CcmnTl- Instill.
I02 tons
37
38
39
40
41
A2
43
J
43
144
J
L
44_
45 4
647
Coke
10 1 tons
48
49
50
i
CAS
ight Vehicle
101 Gals.
r
«U
6j47
48
49
51
INDUSTRIAL FU
Disl. Oil
10* Gals.
52
53
54
OLINE FUEL
Heavy Vehicle
103 Gals.
50
51
52
53
5J
55
5C
:L
57
Resid. Oil
104 Gals.
58
Oil Hiway
I03 Gals.
55
56
57
58
59 60
59
.
61
62
Nal. Gas
I07 Ft.3
63
64
1
Heavy Vehicle
10J GJ'IS.
60
6J62
6J
,i
65J6C
1
Wo<
102I
gUti
)IESEL FU
OH Hrway
104 Gals.
'GsL&elG?
1 1
d
ons
69
EL
RailU
n«
68
i
"1
Process Gas
70
)CO
Ga
70
71
72
notive
s.
71
72
73
71
7'JfTO
1
County
population
73
7- I6|/. >?
^ DuR. 219
a,' 7 2
16 17|t8J19|20J2l|22|23 24 25 26 27 28 29|30 3ll?2 33 :
s fflxl Hofu l/o r y T P
14 35 36 37 38 39 40 41 42 43 44T45 46 47 48 49 50 51J52
_L " " L
53
54
55
56
57
58
59
60
6J.
61
63
64
65
66
djiyzgjzi
n
L3
74
It
76
77
c:
o
~i
70
A
A
-------
AREA SOURCE
Input form
Dale
tote I County
Year
ol
iecoid
_AQCR
z.ala
Name ol Person
Completing Form
mi
Pailiculale
12 13
14 15,16
S02
17 10
19
20
21
NO,
res no2 tons)
4(25
I/
HC
26l27|28|29i30
T7W
CO
31
32
33
3435
I
SULFUR CONTENT (',)
Anlh.
Coal
36
j
37
Bilum.
Coal
38 J39
1
Oist.
Oil
SI
Re
0
42
-J
Oil
Anlh.
Coal
44J45146
TENT ('.)
Bilum.
Coal
47
48
49
Anlh
RESIDENTIAL FUEL
101 ions
50:51152
53
Bitumin.
10 ' tons
54
55
56
57
56
Disl. Oil
104 Gal.
.5?
co
61
62
63
Resid. Oil
104G»I.
64J65
66
67
68
Na
10
09
70
Wood
10J Ions
Anlh.
101 Ions
10lll|l2
T±
13JH
ON
Residential
10 ' Ions
NJIli|l2|l3Tl4
COM
Bilumin.
10 ' Ions
SITI
[75
±n±r
16
n
Tn
lERf IAL AND INS
Disl. Oil
104 Gals.
20
. INCINERATION
Induihul
13? tons
16
17
18
19
20
.?!
Co
1C
fl
??
r\
«
mm. Inst.
? Ions
22127J24
h
1
TITUTIONAL FUE
Resid. Oil
I04 Gals.
25 26
27
28
23
L
Nat. Gas
107 Ft3
.39(31
Residential
10? Ions
25)26
" 1 i
?'l
21
29 bo
32
33
Wood
102lons
34135
Anlh. Coal
10 1 Ions
36] 37
OPEN BURNING
Industrial
10? Ions
31
32
33
3435
|
36
38
39
40
41
Bilum. Coal
10 1 tons
42
Comrn'l- Instill.
10? Ions
37
38
39
40
41
12
43
44
45
46
47
Coke
10 1 tons
48
49,50
i
GAS
Light Vehicle
103 Gals.
43
44
«
46
47
48
49
51
INDUSTRIAL FU
Disl Oil
I04 Gals.
52
53
54
OLINC FUEL
Heavy Vehicle
103Gals.
50
51
52
53
54
§5
JLC
:L
57|
Resid. Oil
10< Gals.
58
.._
[S3
Oil Hiway
103 Gals.
55
56
57
58
59
60
11
Nat. Gas
10' FI.3
?lj§3
64
•'
Heavy Vehicle
103 Gals.
60l
61
6263
:
6'.
65
Gt
Wood
10? tons
12
)I£SEL FU
ON Iliway
10* Gals.
65
16
67
6t
69
Process Gas
10' It3
70.
71
72
EL
Rail Locomotive
104 Gals.
68
69
70
71
77
73
74
75
County
Populalio
103
73
74
T
75
7
76
n
I
77
s
77
C.
70
A
c
n
'•£
tl
70
A
79
A
15
A
Military
LTOCYCIO?
10
11
12.
U
AIRCRAFT
Civil
LTOCYClOl
11
15.
VG
17
10
Commercial
LTOCYClOl
11
20(21
I
I?
23
Anlh. Coal
IQl tons
2J
25
26
27
VE
Diesel Oil
104 cals.
28
29
30
31
SSELS
Resid. Oil
104 Gals.
32
33
34
35
36
Gasoline
IQ3 Gals.
37
38
39^0
EVAPOR
Solvent Purchased
tons yr
41
42
43
1
44
1
45
z
46
0
UION
Gasoline Marketed
IQS Gals.
47
48
49
50
51
Limited Access Road
104 Miles
52.
53
54
65
56
57
MEASURED
Rural Roads
10' Miles
58
.52
6J2
.61
62
63.
/EHICLE MILES
Subuiban Roads
104 Miles
GJ
65
M
iZ
68
c?
Urban Roads
104 Miles
10
Zl
Z2
7J
H
75
71
72
7J
DiM Roads
1 nvclcd
103 Miles
10
11
12 13
1
14
IS
16
Di'l
AirStiips
LTO CYCLES
17
18
19
20
21
Construction
Land Area
10> Acres
22
23
24
25
26
Rock Handling
4 SJoring
101 tons
27
28
29
30
31
FOREST FIRES
Area • Acres
32
33
34
35,
36
/
37
1-
38
J
Quant.
Ion 'acre
39
40
/
41
1
SLASH BURNING
Area • Acres
172
43
44
45
46
47
Quant.
tons acre
48
49
50
FROST
Orchard
Heaters
10*
31
62
53
CONTROL
54
Days
Fired
days yr
55
56
57
Structure
Fi'es
M/year
50
|
59
Z.
60
3
fii
$
COAL REFUSE BURNING
Size ol Byk
10' yard3
62
63
64
65
66
67
»/year
68
69
70
NATURAL SOURCE
(tons)
71
72
73
74
6
75
3
76
l>
77
O
•<
76
A
79
A
COTOEHTS
1^(|ll]l2
1_3
14
O
15
U
16
T
17
|f
18
19
C
20
0
21
U
22
IU
23
T
24
y
25
26
27
28
29
30
31
T2
33
34
35
36
37
38
39
40
41
42
43
44|45
I
46
47
48
49
50
51
52
53
54
55
[5§
57
58
59
60
61
62
63
64
65
66
67
68
f~9h~
72
73
74
75
76
77
.1
C
78
A
/9
A
EPA Dun. 219
3/72
-------
AKEA SOURCE
Input Form
Date
i'213
County
i'l'iuu
Nine ol Peison
Completini Foim
Yen
ol
iecoid
lo] 11
TS
Pailiculate
j_j_.
EMISSION ESTIMATES 110* lonsi
JUZ
§¥
21
22
NO,
23
24
25
/
2G
27
HC
28(29
ll
30
$
31
32
CO
33|3«l35
I |
$
An
Co
36
JLF
th.
al
)7
unco
Dilutn.
Coil
38 J39
1
mm
Disl.
Oil
40J41
1
('.)
Resid
Oil
42|43
1
A5
/
44
HCON
Ulh.
Coal
J5]46
i
TENT IM
Oilura.
Coal
47
48
49
Anlh.
lO'lonj
soisijszjs:
Qitumin.
10 ' tons
54
55
56
i'
5£
RESIDE 111
Oisl. Oil
10< Gil.
59
CO
61
G2
63
Resid. Oil
10* Gil.
IJ63 G4J05
CG
67
llol.
Wood
10* Ions .
Anlh.
I0' Ions
lOlll
R
1
^
«
sid
91 1
12
13
14
COW
Oitumin.
10 ' Ions
15
on SIT
•nlial
3ns
I?
.!«
15
16|17]ia|l9
ICRCIAL AND INS
Disl. Oil
104 Gals.
PO1
1 INCINERATION
Indusliial
I0? Ions
Sff
21
22
23
24
Comm. Insl.
10* Ions
2l|22]23J24
Tfcrr
IITU1IONALFUE
Resid. Oil
I01 Gils.
25l2iB| 27
1 1
20
79
L
Nal. Gas
10' Fl3
30|31
Residential
10* Ions
zslzcbbslzs!
30
32
3:
Wood
10*lons
34J35
1
Anlh. Coal
101 Ions
36J37
!
OPEN BURNING
Industrial
10* Ions
31
32
33
34J35
36
38
39
40
41
Bilum. Coal
10 1 IMS
42
Ccrnm'l • Instill.
10* Ions
37
38
39
40
41
42
43
44
45
46
Lijhl Ve
IO'G
43
44
«
.
47
Did
its.
R
Coke
10 1 ions
48
49<50
i
GAS
e
48
49
51
INDUSTRIAL FU
Oisl. Oil
52 l53|M
OLINC FUE
Heavy Veto
103 Gals
50
5.1
52
J
L
icle
53
5*.
55
5G
:L
Resid. Oil
10* Gals.
r68
OH Hiway
103 Gals.
55
56.
52
51
5960
5J
61
Nal. Gas
10> Fl 3
G2 cUfe!
•'
Heavy Vehicle
I03 Gils.
— Y~\ — 11
. 1
65
6C
Wood
10* Ions
67
Gil 69
1
)IESEL FU
Oil Hiway
10* Gals.
^
G7
Piocess GIS
10' n3
l
-------
|»
k
Y(
0
ice
To
7
)le
!f]
31
1
Oil)
I1.
T
i:
p
12
Anl
lO'lc
iolii
12
County
•ftf
-D
AQC
iU
Tl5
ailiculale
13[ 141
rrr
i.
ns
R
I«
ON
Residential
10 ' Ions
Military
LTOCVC
10
11
2
12
4
10?
13
7
16
17
R
.9.
0
P
EMISSION ESTIMATES llfl? tonsi
>02 NO, HC
19J20
COW
Qilumin
10 ' Ions
15
SIT
16
n
_i_a|i9
21
22
23
24
/
ERplAL AND INS
Disl. Oil
104 Gals.
20
E INCINERATION
Indusliial
10? Ions
16
17
18
AIRCRAFT
Civil
LTOCYC 10l
14
15
S
1C
7
17
3
18
Z-
19
20
21
22
T
23
3
Comm. Ins
10? Ions
—\ T —
>&£
Commercial
LTD CYC 10l
Jl
~
11
22
£
23
J
24
3
t.
1
An
1
^
25
Li
TIT
25
26|2
7 28
UTIONAL
Resid. Oil
26 2
7 28
r"tf
29(30
Z.
CUE
2i
1
CO
3l|32|33 34
L
Nat. Gas
IO7 F|3
30|31 32 3:
"~^T 'o 6
Residential
10? Ions
*
Ih.
OH
25
„(»
Coal
ons
26 2
28
29
30
35
Wood
I0?lons
•H
SULFUR CONTE
Anlh. Bilum. Qi
Coal Coal 0
36
37
38
t
39
40
Anlh. Coal
10 1 Ions
36J37
OPEN BURNING
Industrial
10? Ions
31J32 33
i
34
.35
36
VESSELS
Diesel Oil Resid. Oil
JO4 Gals. io4 Gals.
?28
29
7,
30
1
31 32 33
3 IJ
34
35
36
38
39
40
NT
St.
1
fi
41
C.)
Resid
Oil
42(43
_L
ASH CONTENT (M
Anlh. Gituffl.
Coal Coal
44
15 46
1
47
Bilum. Coal
10 1 Ions
42 43
44
45 46
47
48
49
Anlh
10'lc
SQ'S1
Coke
10 ' Ions
48
49 '50
t
»
CAS
Cemro'l • Instill. Lijhl Vehicle
10? Ions IO1 Gals.
37
38
39
40
Gasoline
IO3 Gals.
f
if
39
•9,
40
ft
41
4243
44
45 46
EVAPOR
Solvent Purchased
Ions yr
41
4243
2,
44
2.
45 46
7V
47
48
49
51
ni
r
Name ol Person
Complel nj Form
Bilumin.
IO1 tons
53
54
15
INDUSTRIAL
Disl. Oil
IO4 Gals.
5~?~
53
54
T
OLINE FUEL
Heavy vehicle
IO3 Gals.
50
51
UION
Gasoline Marketed
locals.
47
SI
49
SSL
5J
52
53
54
55
7
55
5G
FU
5C
Li
5758 5
AREA SO
Input For
Dal
RESIOEN1
Disl. Oil
IO4 Gal.
9 60
'3
:L
Resid. Oil
ID4 Gals.
Msfli
Oil Hiway
IO3 Gals.
56
3
57 585
ftl"
9 60
i
i
-
1
63
1
riAi
64
.FUEL
Resid. Oil
10* Gal.
65
66
Nat. Gas
10' FI.3
PI
63
64
1
Heavy Vehicle
103 Gals.
960
61
6263
•
MEASURED
Limited Access Road Ruial Roads
IO4 Miles IO4 Miles
52.
53
53
53
58
S7585
960
61
62
63
64
65
i
)IE!
Oil
I0<
65
6(
I
EL
(In
Ga
66
I
67
68
C9|
1
Wood
10? Ions
1?
FU
day
Is.
G7
ft
Jjt
§9
un
m
e
CE
Nat. G
107H
70J71
&
as
.3
r
Process (
10' II 3
11
7J
EL
Rail Locomotive
104 Gals.
68
69
VEHICLE MILES
Suburban Roads
104 Miles
GJ,
65
66
i?
68
C9
70
71
/
7?
2.
as
P
Wood . .
74
*
74
7S
a
70
County
Population
IO3
73
74
7
75
7C
?IL/
Urban Roads
104 Miles
70
n
n
7J
74
75
ZE
1
n
S
n
n
H
II
j4
g
5
A
S
•6
70
A
O
25
A
[79
LA]
7.9
A
79
JX
79
A
C
r>o
j
cd
30
J
cd
00
_3
CL
00
4
Di'l Roads
Traveled
IO3 Miles
10
'-
12
13
14
15
16
Dirt
Airstrips
LTO CYCLES
T7]l8jl9
1 1
20
21
Construction
Land Area
W Acres
22
23
24
25
26
Rock Handling
& SJorini
IO1 Ions
27J28
1
29
30
31
FOREST FIRES
Area • Acres
32
33
34
35
/
36
9
37
fy
38
^
Quanl.
ton 'acre
39
40
/
41
|
SLASH BURNING
Area • Acres
42
43
I
44
2
45
5
46
?
47
|
Quant.
tons acre
48
49
50
T
FROST CONTROL
Orchard
Healers
to2
iL
"
53
54
Days
Fired
days yi
5E
56
57
Structure
Fires
-------
Stale j
Yra<
cl
iecord
10
1P_
"1
11
1C
TT
ii
i
n
County
Paiticula
12
Ant
lie
tt
win'
LL
i.
MS
13|K
1
ONS
•jidenlial
]' Ions
12
Military
LTOCYC
LLL
Dirt
"i
103
10!
]
11
!?.
13Tl4
1
I02 LI
13 14
Roads
velcd
Miles
n]i4 i
~1
COMMENTS
EPA
/)
5
Oun
V7J
13 14
219
AQCR
jf, 7.
O o
t
15.16
f
17
fel
•
ia
f.f,
oz
^
J±n_
cow
Bitumin.
10l tons
15[lii
^
ISS
t
En
20
ITE INCINERATION
Industrial
132 tons
15 16
17
18
AIRCRAFT
Civil
0 CYC 10'
.5.16
5(16
1
/
LT
"1
15 16
i ^
17
10
,9
C
L
5
20
101
2,
ESTIMATE
NO,
_. _L.L1
flAL AND INS
Oisl. Oil
Ifl4 Gals.
21
1?
?3J?«
Comm. Insl.
10? Ions
onimcrc
TOCY
2ol"21
Dirt
\\l Sl/ips
0 CYCLES
li
«l
C.
19 20
21
Tsl
o
20
U
21
A
«»5
ial An
ClOl 1
*M
S (102 tons)
HC
25 26J27|28(2
IITUTIONAL FU
Resid. Oil
101 Gals.
25 26 27 28 2
Residential
102 Ions
25 26 27J28J2E
ITU
h. Coal Die:
Ql tons 1Q4
25 26 27 28 2j
3 30 3l|32
..'4.J .
EL
Nal. Gas
107 Ft3
3 30|_31
32
CO
3:
Wood
102lons
34j35
I
SULFUR CONTENT
Anlh. Bilum. Disl.
Coal Coal Oil
36 17
38
39
40
11
Anlh. Coal
10 1 tons
3§j37
38
39
40
41
f.
Re
0
^
42
OPEN BURNING
Industrial Ccmm'l Instill.
10? Ions Id2 Ions
(30 31
Jj-J
VE
el Oil
Gals.
) 30 31
Conslruclion Rock Handling
Land Area & SJoring
Iff Acres 103 Ions
22
23 24
22
r
2324
y
25 26 27 28 2<
25 26 27 2a[2
~ ±
1 30:31
I
i
a
SSE
32
33
I
36 37
38
39
40
LS
Resid. Oil Gasoline
104 Gals. I03 Gals.
33
3435
3J. 37
38
FOREST FIRE
Area • Acres
32
3 30 3ll:7
33
33
34 3$
36 37
7
I34 35
36 37
38
(*
38
39
40
41
42
Sid
il
43
.
ASH CON
Anlh.
Coal
1 T
,
Bilum. Coal
10 1 tons
43
44 45
LijIV
43
44 45
16
FENT («
Bilun
Coal
4^48
1
47
,)
.
49
Anlh.
ID1 Ions
50151152
Coke
10' Ions
48
49J50
i
GAS
Vehicle
Hals.
46
47
EVAPOR
Solvent fVirchased
tons yr
41
S
Quint.
Ion 'acre
39
39
40
Jl^
41
I
42
f
?f
t
48
49
51
53
Name ol Per
Complelinj
Oitum n.
ID1 Ions
54
65
INDUSTRIAL
Disl. Oil
10* Gals.
52
53
54
OLINC FUEL
Heavy Vehicle
103 Gals.
GO
51
\TION
Gasoline Marketed
IflScals.
42
SLASH BURNII
Area • Acres
42
4ol
41
42
43
4445
43
4445
r"
46
46
47
47
48
19
50
(G
Quant.
tons ac«
48
48
49
50
49
50
5J
52
53
54
50
56
FU
lc
57
ion
Form
AJIEA
Input
RESIDENTIAL FUEL
Oisl. Oil Resid. Oil
104 Gal. |04 Gal.
58 59 60
:L
Resid. Oil
. l04Gals.
57k8|l9l60
i • !
61 6
1
6.1 P
2 63 64JG5
: JI
66
Nal. Gas
Ifl7 Fl.3
? 63 64
1
Oil Hiway Heavy Vehicle
103 Gals. 103 Gals.
55
56
57
Limited Access Road
10 4 Miles
&2
&3
FROST
Orchard
Heaters
102
il
51
52
52
53
53
54
CO
54
15
56
57
HROL
Days
Fired
days yr
5E
54
55
56
57
58 59 60
61 6216316'!
rn
-6.5
-
67
1
.
)IES£L FU
Oil Hiway
!04Gals.
65
66
67
1
68
Wa
)?
I
EL
R!
6~81
SOUR
Form
Date
CE
Nat. Gas
107 II.3
69 70
>d P
ons
§1 7>
71 72|73
rocess 1
107H3
71 ?j?
il Locomotive
104 Gils.
6970
1
MEASURED VEHICLE MILES
Rural Roads Suburban Roads
ID4 Miles ID4 Miles
§9 59 GO
Structure
Fires
tf/yeaf
58 59 60
I 1 2
56
57
58 59 60
Sli
2 63. 6J
6.5
C6
67
COAL REFUSE DL
Size ol Oyk
10' yard3
"Rie
1
61 6
26364
2 63 64
65
65
66
66
67
67
68
69 70
RNING
«/y_ear
G8|69fTt:
G8
65J70
71 72
las
P
flood
102 Ions
74(751716
. I L.
7-l|?5j7CJ77
County
Population
V3
7417&7G
WhW
Urban Roads
104 Miles
11 1.71
NATl
(t
71 72
^n
7J
7J 75 7C
1
Ti
RAL SOURC
ons)
73!
74l75 7SJ77
zrefr
73
74 75 76
77
C
g
ti
«£
76
.A
c.
ft
' u
; *•*
A
«T
O
•£
•*c
7l)
A
C
O
"o
^
29
A
:E
CT
C*
O
;e
A
£
«i
7.0
A
Lai
70
A
A
A
79
A
/i
A
C
Tu
1
Ci
8.1
2
C'
Hi
Cc
0.0
4
DC
e-
cd
59
6
-------
AREA SOURCE
Input Form
Date —
Sine
County
AQCR
Name ol Person
Completing Foim
Yeai
ol
lecoid
10] 11
"
Particular
EMISSION ESTIMATES HO2 lonsi
502 NO, HC
17
30
3
31
— -1
, — l
32
"
CO
33J34J35
-•
1
SULF
Anth.
Coal
36
, —'
J7
URCO
Bitum.
Coal
38
39
YTENT
Disl.
Oil
40J41
I
IM
Resid
Oil
42 [43
I
ASH CON
Anlh.
Coal
44|.|5J46
J |
TENT IM
Bilum.
Coal
47
48
49
Anlh.
10* tons
50:51152
1
53i
Bilumin.
ID1 Ions
54
55
56
57
5E
RESIDEN
Oisl. Oil
104 Gal.
59
60
61 62
1
63
flAL FUEL
Resid. Oil
104 Gal.
64JG5
1
66
67
68
Nat. Cas
107 II.3
69f70
_J_
71
72J73
Wood
lO^tons -.
74
75
76
77
78
7.9
~ib
Anlh.
|Q> Ions
!0ll1 12
1
1
flesid
io't
»i r
1 1
13
fnli
ins
fl
14
ON
al
J«
COM
Bilumin.
10 ' Ions
15
SIT
[75
16
17
18
Tg"
1
ERplAL AND INS
Disl. Oil
104Gals.
20
: INCINERATION
Indusliial
I02 tons
1.6
17I
18
19
20
21
Co
1C
"1
2?
23
24
mm. Insl.
2 tons
22
1
?3J?<
TITUTIONAL FUE
Resid. Oil
ID1 Gals.
25
26
27
20
23
L
Nat.
107
30
Residential
102 Ions
25.126 J27j
28
29
3.0
111
Gas
FlJ
I?
33
Wood
102lons
r34
35
Anlh. Coal
10' tons
361
OPEN BURNING
Industrial
10? Ions
Ml
32
33
34
35
36
37
38
39
40
41
Bilum. Coal
10 1 tens
^42
CcirwVI- Instill.
102 Ions
37
38
39
40
41
12
43
44
45
46
47
Coke
101 tons
48
49J50
GAS
Light Vehicle
10 J Gals.
43
44
45
46
47
48
49
51
INDUSTRIAL FU
Disl. Oil
ID4 Gals.
521
53
OLINE FUEL
Heavy Vehicli
103 Gals.
sol
51
52
53
L"
.
54
55
5C
EL
a
1
Resid. Oil
104 Gals.
4
1?
Oil Hiway
103 Gals.
55
56
57
58
59
60
61
02
Nal. Gas
107 Ft.3
63
64
1
Heavy Vehicle
103 Cats.
6?
61
62|63
6
26
27
VE
Diesel Oil
104 Gals.
28
29
30
11
SSELS
Resid. Oil
104 Gils.
32
33
34
35
36
Gasoline
103 Gals.
37
39
39
40
EVAPOR
Solvent Purchased
Ions yr
41
42
43
44
$
45
5
46
^
\rioN
Gasoline Marketed
IQScals.
47
48
41
50
51
Limited Access Road
I04 Miles
52
S3
54
55
56
57
MEASURED \
Rural Roads
104 Miles
58
59
60
6J.
62
63
/EMICLE MILES
Suburban Roads
104 Miles
.6J
.65
65
67
.OS
69
Urban Roads
104 Miles
70
Zl
71
7J
H
75
LC
20
19
ao
Dirt Raids
Traveled
103 Miles
10
11
12
13 14
1
1
IS
16
Dirt
Airstrips
LTO CYCLES
17
18 19
1
20
21
Construction
Land Aiea
IV Acres
22
23
24
25
26
Rock Handling
& Sjorinj
103 Ions
27|28
I
29
30|31
|
FOREST FIRES
Area • Acres
32
33
34
35
36
/
37
V
38
5
Quanl.
ton 'acre
39
40
I
41
I
SLASH BURNING
Area • Acres
42
43
44
45
46
47
Quanl.
Ions acre
48
49
50
FROST CONTROL
Orchard
Heaters
51
62
53
54
Days
Fired
days yr
55
66
5:
Structure
Fires
»/year
58
59
1
60
H
R1
2.
COAL REFUSE BURNING
Size ol Bvk
10'yard3
62
63
64
65
66
67
tt/year
68
69
7C
NATURAL SOURCE
(tons)
71
72
73
74
3
75
3
70
?
77
-------
Stale
i ! •>
lj.2
Year
ol
{((Old
loin
Counly
I
JL£J
1
.=.
--
AQCR
'oi8]"]'!'
EMISSION ESTIMATES HO2 tonsi
Pailiculale
12.1131
14
15
16
S02
1 r T 1
17 10 19 20 21
22
NO,
a
2-i
25
0
HC
26
27 2
8 29
V
30 3
/
COUlERf IAL AND INSTITUTIONAL FUEL
Anlh.
IO1 Ions
10 [ill 12! 13J 11
It
•sidrnti
ON
al
Bilumin.
10 ' Ions
15
16
» lib? ?
Dut. Oil
10* Gals.
0?J
22
23
24
SITE INCINERATION
10 ' Ions
iffy.
.!_
1213
,4
16
16
Industrial
IO2 Ions
17J18 19 ?
1
Comm.
Inst.
IO2 Ions
0 21
22
AIRCRAFT
Military
LTOCYC 10?
10JVT
1?.13
Civil
LTOCYC
,4
15 1C
23
^
Commercial
10' LTOCYCIO'
TTllB 19 2
" _i n~ " :
I
22
23
*
Resid. Oil
IO1 Gals.
15
26
1'
0 23
1|32
I
CO
33
34
Nal. Gas
10
3pl3
'Ft3
1.3?
3:
35
Wood
I02lons
3335
SULFUR
Anth.
Coal
36
}7
CONTENT (M
Bilurn.
Coal
38|39
Anlh.
Oisl.
Oil
40|41
Coal
Resid
Oil
42|43
10 > Ions
36
37
38
39
40
OPEN BURNING
Residential
IO2 Ions
25
Anlh.
,
27JI
Coal
10' Ions
24
»
26
272
J.2?po.3
Industrial
IO2 tons
1 32
33
34
VESSELS
Diesel Oil
10< Gals.
B 29
3013
132
Resid.
35
36
41
ASH CONTENT (M
Anth.
Coal
d
.5
,
Bitum.
Coa
47(48
49
„
Anlh.
10 1 Ions
50lB1j5?|53
Name ol Person
Com
Meting Form
Bitumin.
10'
54
55
INDUSTRIAL
Bilum
Coal
10 1 Ums
42 43
__
Ccmrn'l- Instill.
!44
"
45
46
47
Coke
10' tons
48
49j50 51
1
Ions
56
57
ii
AREA SOURCE
Input l:orni
Date
RESIDENTIAL FUEL
Disi. Oil
10< Cal.
5_9
60
FUEL
Dist. Oil
10^
5.2 to
1
Gals.
54
55
56
Resid. Oil
10* Gals.
t •
GASOLINE FUEL
Lilhl
IO2 Ions
37
38
Oil
IO4 Gals.
33
34
3$
36
39
40
Gasoline
ID3 Gals.
32
38
39
40
41
42 43
44
10
45
Vehicle
1 Gals.
46J47
48
49
Heavy Vehicle
IO3 Gals.
5051
EVAPORATION
Solvent Purchased
tons yr
41
42 43
j[
44
3
45
3
46
2_
Gasoline Marketed
105 Gals.
47
40
i?
50 SJ;
«
,
54
55
Oil Hiway
IO3 Gals.
56
57
58
59
61
60l_61
62
i?
Resid. Oil
10* Ol.
I i r
64 65 66 67J68
"iizlit
i
Nal. Gas
107II
wjlfijzi
3
l\
73
Nal. Gas Wood Process Gas
10' Ft.3 IO2 Ions 10' N 3
62
63
64 65 JK 67 Oil
§9 70 71
DIESEL FULL
72
Heavy Vehicle Oil Hiway Rail Locomotive
IO3 Gals.
60
61
~
6?
«
10< Gals. IO1 Gals.
[64 esjee G7 68
1
69 70 71
7?
73
Wood
102lons .
Z4
.y
75
1"
76
11
o
It
•rf
7J
-A
79
..A
c
J
7_C
Counly
Population
IO3
73
74
2
,,
7u
r
I
MEASURED VEHICLE MILES
Limited Access Road
10< Miles
52
^
14
55
56
S2
Rural Roads
10* Miles
58
59
60
61
62
63
Suburban Roads Urban Roads
10* Miles
64 65 Ccfr37 68
"IL
69 70 71
104 Miles
72.
13
74
75
1$.
'12
O
' w
!**
.Z8
A
7.3
A
C"
0(
2
s
12
o
f>
It
VU
A
79
A
t-
-[
'-'•
o
tJ
*i
29
A
79
A
c
C.Q
4
Did Roads
lovcled
IO3 Miles
10
11
12 13 14
I !
15
16
Did
Air Slfips
LTD CYCLES
vinifFjl'9
20
21
Conslruclion
Land Area
IO3 Acres
22
23J24
I
25
26
Rock Handling
& SJorinf
10J tons
27|28
I
29
30
31
FOREST FIRES
Area • Acres
32
33
34
35
36
37
38
7
Quanl.
Ion 'acre
39
40
f
41
1
SLASH BURNING
Area • Acres
42
43
44
45
46
47
Quant.
tons acn
48
49
50
FROST CONTROL
Orchard
Healers
IO2
i1
52
53
54
Days
Fired
days yr
56
56
57
Structure
Fires
0/year
58
59
?
60
8
R1
6
COAL REFUSE BURNING
Site ol Bank
102yaidJ
62
63
64
65
66
67
(f/yjtai
68l69f7li
1 1
NATURAL SOURCE
(tons)
71
72
73
74
2.
75
T
76
0
77
I
CT
U
«<
/8
A
73
A
C'
DC
£
COfiMEHTS
10J11 12J13Tl4 15 16 17 is[
S\o id&K ser~\
EPA OUR. 219
3/72
llHzj J2 23
24
1
25
26
27
1§
29.
30
31 1^2
r
3J
34
35.
36
37_
38
31
40
il
42
43
4445
46
47
48
49
50
M
52
53
54
55
56
57
58
59
60
61
61
O
64
65
66
67
60
ssbjzi
7J
7.4
rD
76
7j
1
«c
70
A
A
(t
-------
AREA SOURCE
Input form
Dale
Sine
Year
ol
tecoid
11
County
AQCR
iR
Particular
12
s
16
EMISSION ESTIMATES (10* tonsi
S02
17
10
NO,
HC
26
27 28 2930
.!,«"
rr
31
32
CO
33
3435
SULFUR CONTENT (M
Anlh.
Coal
36
J7
Bilum.
Coll
38
39
Disl.
Oil
40Jin
Resid
Oil
ASH CONTENT |M
Anlh.
Coal
Bilum.
Coal
47
48
49
Anlh.
101 Ions
Name ol Peison
Completing Form
Bitumin.
10' tons
54
55
5C
57
58
RESIDENTIAL FUEL
Disl. Oil Resid. Oil
104Gal. - 104Gal.
59
60
61
"
62
63 64J65
it±
66
67
68
Nat. Gas
107 It.3
7071
Wood
10? Ions
74
75
78
15.
LAlA
Anlh.
10 1 tons
10ll1 12
l
13|l4
COMA
Bilumin.
10 ' tons
15
OH SIT
Residential
10 ' Ions
!£.U|«
314
*
16
17
18|19
i
ERCIAL AND INS
Disl. Oil
10< Gals.
?0
: INCINERATION
Industrial
102 Ions
16
17
18J19
1
20
?1
??
£
23
^
24
B
Comm. Insl.
102 Ions
......
24.
TITUTIONAL FUE
Resid. Oil
104 Gals.
25 26
27
a
20
1
23
H
L
Nat. Gas
107 Ft3
30
—
Residential
10? Ions
tl
-"1
28
29
30
31
32
3
33
Wood
3335
I
Anth. Coal
10 'ions
36J37
OPEN BURNING
Industrial
102 tons
3.1
3J
I?
34J35
i —
36
30
39
40
I
41
5
Bilum. Coal
10 1 Ions
42
Ccmn'l- Instill.
102 Ions
37
38
39
40
41
.12
43
44
45
46
1"
47
t
Coke
10 1 Ions
48
49JSO
GAS
Light Vehicle
103 Gals.
43
44
45
46
47
48
49
51
INDUSTRIAL FUI
Oist. Oil
I04 Gals.
52
54
OLINE FUEL
Heavy Vehicle
103 Gals.
50
51
52
53
54
55
SC
:L
Resid. Oil
104 Gals.
1?
ssjeplsi
Oil Hi way
103 Gals.
55
56
I
57
£
58
59
6
02
Nat. Gas
107 Ft.3
63
64
•• • 1
Heavy Vehicle
103 Gals.
60 61
62|63
64
65
J_
6(
lo
Wood
102 Ions
67
)IESEL FU
Oil Iliway
104Gals.
65
66 67
1*15
1
§?.
Process Gas
lO'll3
7Q
12
EL
Rail Locomotive
10* Gals.
60
69
70
/
71
6
72
^
73
74
75
76
County
Population
7_3
74
75
1
7C
T
77
s
Tl
J
38
A
g
fi
78
A
7.?
A
A
C
81
•
C
9'
Military
LTD CYC 10?
10
11
12
13
AIRCRAFT
Civil
LTOCYClOl
14
15
16
7
17
(,
18
^
Commercial
LTOCYCIO'
19
20J21
|
22
23
Anlh. Coal
10l tons
24
25
26
27
VESSELS
Diesel Oil
10< Gals.
28
29
30
31
3
Resid. Oil
ID4 Gals.
32
33
34
35
36
Gasoline
10.3 Gals.
3?
/
38
0
39
5
40
(3
EVAPORATION
Solvent Purchased
Ions yr
41
42
43
I
44
1
45
T
46
6
Gasoline Marketed
105 Gals.
47
48
49
50
51
Limited Access Road
10< Miles
5?
53
64
55
56
57
MEASURED VEHICLE MILES
Rural Roads
I0< Miles
50
59
60
61
62
63
Suburban Roads
10* Miles
^64
65
66
67
68
69
Urban Roads
104 Miles
70
71
72
73.
v\
75
?e
7?
n
0
u
«<
70
A
79
A
Dirt Roads
1 raveled
103 Miles
10
11
12
13
14
IS
16
Djfl
Ail Strips
LTD CYCLES
17|18
I
19
20
21
Construction
Land Area
\ff Acres
22
23
24
25
26
Rock Handling
t SJoring
103 Ions
27
28
29
30
31
FOREST FIRES
Area • Acies
32
33
34
35
36
37
7
38
V
Quant.
ton 'acre
39
40
/
41
/
SLASH BURNING
Area • Acies
42
43
44
45
46
47
Quant.
tons acic
48
49
50
FROST CONTROL
Orchard
Healers
, 10*
i1
62
53
54
Days
Filed
days yr
5E
56
67
Structure
Fires
ttjjta
58
59
^
60
6
M
2.
COAL REFUSE BURNING
-
Sue ol Bjpk
10'jard3
62
63
64
65
66
67
H/yjar
60
69
7C
NATURAL SOURCE
(tons)
71
72
73
74
5
75
9
76
Z
77
V
c
•I
n
A
79
A
COIMENTS
1olll]l2J13
ilujsls
14
F
15
Y
16
17
C.
18
6
m?o
i>|A/
21
T
22
Y
23
24
25
26
27
28
29
30
31 C2
33
11
35
36
37
38
39
40
H
42
43
44
45
46
47
48
49
50
51
52
S3
54
55
56
57
58
59
60
61
62
63
64
65
66
67
6G
69|70J71
Zl
73
74
76
76
Z7
g
s
78
A
/9.
A
(U
EPA OuR 219
V7J
-------
SI
1
2>
Yl
0
!ec
ion
lie
fl
ar
1
oid
11
bis
1C
1
10_|1JI_
_L
10
1-
i
r
12
Anil
1 lo
«"
County
arlicula
E
.
us
t
OH!
Residential
10 1 Ions
J.!
Mili!
L10C
10
n
12
L
Jiy
YC
R
13H
1.11
10? LT
131<|
1
AQCI!
le SC
r
15.16
J_
I
1
33
ITE III
IE 16
EMISSION ESTIMATES 110*
2 NO,
ulialiglzo
1 r
CO
ilinnin.
> tons
r
|
WilER
.?. ?P
CINERATION
Industrial
la2 Ions
Trjia 1
AIRCRAFT
Civil
OCYC Ifll
I5J16
_L
•17 18 1
9J20
1'
Ui
10
21
22
23
LAND
si. Oil
1 Gals.
22
23
24
I
INS
24
Comm. Insl.
I02 tons
yk
Commercial
LTOCYC10
9 20
2,
22
fe
i
:
h
An
i
2J
25
\L
TIT
25
26
lonsi
HC
27 28|29
3>
UTIONAL FUE
Resid. Oil
26
27
20
23
1
L
M
i
31
32
CO
33
al. Gas
0' Ft3
3p|31
Residential
102 Ions
ff
Ih. Coal
Ol tons
15
26
27
M
29
30
3_?
M
34
35
Wood
102lons
34
J*
SULFUR
Anth. Bit
Coal Co
36
36
OPEN BURNING
Industrial
102 tons
31
VE
Diesel Oil
)04 Gals.
M
29
30
31
32
33
34
35
1
36
SSELS
Resid. Oil
104 Gals.
32
33
34
as
36
[17
38
CO
jm.
al
39
Ions
42
Ccmni'l- Instill.
102 Ions
37
38
3_9
40
Gasoline
103 Gals.
32
38
39
40
41
*-
43
44
45
Li(hl
10
!i
44
45
46
47 48 49J>0
1
,. 1 ,
GAS
Vehicle
1 Gals.
46
EVAPOR
Solvent Rjrctused
Ions yi
11
1?
43
7L
44
"0
45
Z
46
8
47 48 49
OLI
He
1
5.0
51
NE
avy
O3
5J.
UION
Gasoline Marketed
105 Gals.
:«[^9
50
51
nj
fl
53
Name ol Person
Complelinj Foin
Dilumin.
10 ' Ions
54
55
INDUSTRIAL
Dist. Oil
104 Gals.
5?
FU£
Vch
Gals
!
L
id
53
i
54
56
FU
"Up
55
57
:L
5£
n
AREA SOUR
Input (:orni
Date
RESIOEN1
Oisl. Oil
104 Gal.
59
60
Resid. Oil
104 Gals.
_5J|1?
Oil Hiway
103 Gals.
56
57
Limited Access Road
10 4 Miles
52
52
i4
5J>
56
57
58
59
60
61
61
6263
!
62
IAL FUEL
Resid. Oil
104 Gal.
_64J65
Nal. Gas
107 Ft.3
1?
64 .65
DIE!
Heavy Vehicle Oil
103 GalJ. 10^
CO
6162
1
63
MEASURED
Rural Roads
104 Miles
58
52
CO
61
62
63
6J 65
66
6C
EL
Hiv
Ga
16
67
C8
Na
10
S9
Wood
10? Ions
67
FU
»ay
Is.
67
St.
69
10
CE
1. Gas
Process (
10' II3
7QJ7.1
72
EL
Rail locomotive
101 Gals.
G8
69
VEHICLE MILES
Suburban Roads
104 M
.70
A
O
t;
?J
A
C
0
X*
7.0
A
79
A
79
A
79
A
c
C
c
(ji
c
P.I
4
Dirt Roads
lovclcd
101 Mi
12J13
I
es
14
15J16
I
Did
Airstrips
LTO CYCLES
I7|l8|l9
I I
20
21
Construction
Lijnd Area
22
O5 Acres
23
24
2526
I
Rock Handling
{
, Slorinj
10J tons
27
28
29
30
31
FOREST FIRES
Area • Acres
32
33
34
35
36
37
38
Quant.
ton 'acre
39
40
41
SLASH BURNING
Area • Acres
42
43
44
45
46|47
I
Quanl.
tons acre
48
49
50
FROST CONTROL
Orchard
Healers
10*
31
52
S3
54
Days
Fired
days yr
5E
56
57
Structure
Fires
W/year
50
I
59
4'
60
Z
R1
6
COAL REFUSE BURNING
Si;e ol B¥ik
10'yard3
62
§1
64
65
6C
67
(f/year
CSJJBspt
NATURAL SOURCE
(tons)
7lT72
1
73 74
I/
75
O
76 77
5|o
c.
•^
18
A
79
COIMEHTS
10 11 12 13 14
JJ
15
16
C
17
b
18 19 20
o l/ulT
21
Y
22
23
2425
1
26
27
28
29J30
31 b
|
33
11
35
36
37
38
39
40
41
42
43
44 45
1
46
47
48
49
50
51
52
53
54
55
56
S7
58
59
60
61
62
63
6*.
.65
6§
67
68
69170 '71
1 |
72
73
74
75
«
Z?
/9
£PA OuR. JI9
V72
-------
AREA SOURCE
Input Form
Date
Slate
-i|l
ILL.
Year
ol
(ecoii)
IpTvi
County
m
ffl
AQCR
m
EMISSION ESTIMATES HO2 tonsi
Pailiculale
llll3
uTs^ie
, J
_«Jz
ITflflllgjIo^l
zt±±£
NO,
i?Ji3
24J25
ma
i
2J5J27J2
Name ol Person
Completing Form
10? tonsi
HC
2J5J27J28
29J30
5IQ.
31
32
CO
3334
35
SULF
Anlh.
Coal
36
57
"URCO
Biturn.
Coal
38 J39
1
NTENT
Dist.
Oil
40J41
i
(M
Resid
Oil
42J43
1
ASH CON
Anlh.
Coal
44
•15 46
1
TENT (M
Qitum.
Coal
47
48
49
Anlh.
10* Ions
50':5li52]53
.. 3f°H
Bitumin.
10' tons
54
5E
56
57
58
•^
RESIOEN1
Disl. Oil
104 Gal.
59
T
61
5
6?
63
HAL FUEL
Resid. Oil
104Gal.
64] 65
1
66
67
68
£•
Nat. Gas
107 It.3
69
70
71
7273
W
Weed ,
102tons .
74
7576
1
77
3
|
IA
n
.A
t
BO
J
COMMERCIAL AND INSTITUTIONAL FUEL
Anlh.
101 tons
10)11
i ,
12
13
1«
Bitumin.
10 ' Ions
15
16
17
18119
Disl. Oil
104 Gils.
201
21
22
7
23 24
50
ON SITE INCINERATION
Residential
10 ' Ions
ioTn
.11
«
_
,3
14
15
Indusliial
10? Ions
16
17
18
19
20
Comm.
Insl.
10? Ions
21
22
23 U
,112-
Resid. Oil
104 Gals.
25
26
27J28
315
23
i
Nat. Gas
107 Ft3
30|31
32
H
3"
5
Wood
102lons
^34
35
t INDUSTRIAL FUEL
Anlh. Coal
10 > Ions
36
37
38
39
40
4
41
1
Bilum. Coal
10 1 tons
42
OPEN BURNING
Residential
102 tons
2B|26b7J28J
29
:±1±1:_
30
Industrial
10? tons
31
32
33
34
l
35
36
ComnT Instill.
10* tons
37
38
39
40
41
42
43
44
45
46
5
47
3
Coke
10 1 tons
48
49150
1
1
51
Disl. Oil
104
52
53
Gals.
54
GASOLINE FUEL
Light Vehicle
101 Gals.
43
44
45
46
47
48
49
55
5C
1
Resid. Oil
104
57! 58
Heavy Vehicle
103 Gals.
50
51
52
53
54
Gals.
59] COl 61
! I
Oil Hiway
103 Gals.
55
56
1
57
^
58
59
3
62
Nat. Gas
10* Ft.3
63
64
65
GC
Wood
10? Ions
67
6u1
69
Process Gas
10?ll3
70
71
72
DIESEL FUEL
Heavy Vehicle
60
ID3 Gils.
61
62|63
61
Oil Hiway
!04Gals.
65
66
13
67
3
Rail Locomotive
104
60
69
Gals.
70
"2.
71
6
72
3
73
74
75
70
County
Population
1
73
?«
)3
75
«
7C
77
.S
! *-*
78
•A
19
A
CL
8(
2
s .
f
£
7;
6
t>
78
A
79
A
C'
UC
3
AIRCRAFT
Military
LTOCYC10?
10
11
12
13
Civil
LTD CYC 10'
14
15
2
16 17 18
i]J_LL
Commercial
LTOCYC10'
19
20121
1
22
23
VESSELS
Anth. Coal
10l Ions
24
25
26
27
Diesel OH
10< Gals.
28
29
30131
Resid. Oil
104 Gals.
Ill
33
34
35
36
Gasoline
103 Gals.
37
38
39
B
40
M
EVAPORATION
Solvent Fuichiised
tons yr
41
42
43
44
45
3
46
7
Gasoline Marketed
105 Gals.
*7
48
49
50
51
MEASURED VEHICLE MILES
Limited Access Road
10 4 Miles
52
53
54
55
56
57
Rural Roads
104 Miles
58
59
60
61
62
63
Suburban Roads
104 Miles
64
65
66
67
68
69
Urban Roads
10* Miles
70
71
7?
7?
74
75
7C
77
C
o
£
78
A
79
A
C'
00
4
Dirt Roads
Traveled
103 Miles
10
-
12
13 14
!
15 16
1
Dirt
Ail Strips
LTO CYCLES
1 1 1
21
Construction
Land Area
\ff Acres
22
23
24
25
26
Rock Handling
i SJoring
27
10' Ions
28
29
30
31
FOREST FIRES
Area • Acres
32
33
34
3?
36
37
1
38
1
Quant.
ton 'acre
39
40
1
41
|
SLASH BURNING
AIM • Acres
42
43
44
45
46
47
Quant.
Ions acre
48
49
50
FROST CONTROL
Orchard
Heaters
10
J1
52
53
54
Days
Fired
days yr
55
56
67
Structure
Fires
»/y
58
59
ear
60
4
K1
3
COAL REFUSE BURNING
Site ol Bwk
10'yaid3
62
63
64
65
66
67
K/year
68
69
K
NATURAL SOURCE . .
(tons)
21
72
73
74
75
76
3
77
7
r.
•X
78
A
79
A
Ci
UO
E
COMMENTS
10J11
m
12
I?
13 14
*k
15
A/
16
17
C
18
0
19
if
20
A/
21
r
22
Y
23
24
25
26
27
28
29
30
31 C2
i
33
34
35
36
37
38
39
40
41
42
43
44UI5
I
46
47
48
49
50
51
52
53
54
55
56
57
58
59
60
61
62
63
64
65
6J
67
ii
69|7JJ7J
12
L3
74
75
76
7J
I
71
A
/9
A
cd
no
6
EPA OuR. 219
J/72
-------
APPENDIX B
COUNTY ACTIVITY PARAMETERS
-------
TABLE B-l
ASPHALT USAGE IN NEW JERSEY
1975 1977
(TONS) (TONS)
Cutback 26,458 33,003
Emulsified 55,357 10,409
TABLE B-2
PESTICIDE ACTIVE INGREDIENTS FOR NEW JERSEY
1976
(POUNDS)
Atlantic
Bergen
Burlington
Camden
Cape May
Cumberland
Essex
Gloucester
Hudson
Hunterdon
Mercer
Middlesex
Monmouth
Morris
Ocean
Passaic
Salem
Somerset
Sussex
Union
Warren
356,332
147,539
563,590
238,807
38,884
350,414
122,709
875,809
68,484
183,162
166,848
219,895
401,716
126,942
79,290
57,834
287,457
120,975
142,940
77,921
177,603
B-l
-------
TABLE B-3
Atlantic
Bergen
Burlington
Camden
Cape May
Cumberland
Essex
Gloucester
Hudson
Mercer
Middlesex
Monmouth
Morris
Ocean
Passaic
Salem
Somerset
Sussex
Union
Warren
NEW JERSEY
1975
10,995
249
10,579
5,381
4,464
4,464
+
2,399
416
+
8,429
2,149
1,857
21,075
1,075
2,065
63
825
+
825
TIMBER CONSUMED
(TPY)
1977
87,265
1,966
84,000
42,667
35,436
35,436
+
19,025
3,282
+
66,923
17,060
14,760
167,333
8,530
16,410
649
6,564
+
6,564
BY WILDFIRE
1982
28,322
533
35,702
18,126
6,664
41,650
-
8,097
1,391
-
26,438
7,247
6,272
61,642
3,623
6,964
274
2,762
-
2,782
1987
28,332
39,550
39,550
20,092
6,664
41,650
-
8,946
1,549
-
31,504
8,030
6,947
76,636
4,023
7,715
306
3,098
-
3,098
No wildfires occurred.
No wildfires projected.
B-2
-------
TABLE B-4
Atlantic
Bergen
Burlington
Camdem
Cape May
Cumberland
Essex
Gloucester
Hudson
Hunterdon
Mercer
Middlesex
Monmouth
Morris
Ocean
Passaic
Salem
Somerset
Sussex
Union
Warren
TONS OF
1975
2,760
0
16,803
0
1,987
1,370
0
0
0
0
0
0
0
0
12,581
0
0
0
0
0
0
PRESCRIBED1 BURNING
(TPY)
1977
6,463
0
14,867
0
3,026
1,697
0
432
0
0
0
0
115
0
14,195
0
0
0
0
0
21
IN NEW JERSEY
1982
16,560
0
32,200
0
5,290
6,440
0
0
0
0
0
0
598
0
19,780
0
0
0
161
0
230
1987
22,080
0
43,700
0
5,290
6,440
0
0
0
0
0
0
828
0
17,940
0
0
0
184
0
322
See Chapter VI.
B-3
-------
TABLE B-5
Atlantic
Bergen
Burlington
Camden
Cape May
Cumberland
Essex
Gloucester
Hudson
Hunterdon
Mercer
Middlesex
Monmouth
Morris
Ocean
Passaic
Salem
Somerset
Sussex
Union
Warren
NEW JERSEY AGRICULTURAL
INFESTED
22
1
22
9
0
12
0
34
0
5
7
2
3
3
1
3
6
2
13
0
56
BURNING PERMITS
HERBACEOUS
2
1
2
0
2
4
0
13
0
2
1
1
2
14
2
0
12
8
10
0
5
ISSUED IN 1977
ORCHARD PRUNINGS
13
13
15
5
0
4
0
13
0
18
9
6
6
24
3
3
4
16
16
0
13
B-4
-------
TABLE B-6
STRUCTURAL FIRES IN NEW JERSEY
Atlantic
Bergen
Burlington
Camden
Cape May
Cumberland
Essex
Gloucester
Hudson
Hunterdon
Mercer
Middlesex
Monmouth
Morris
Ocean
Passaic
Salem
Somerset
Sussex
Union
Warren
1975
1,496
1,728
1,112
2,990
177
409
5,001
479
1,022
107
1,732
1,853
1,238
1,216
441
1,121
142
486
262
1,428
63
1977
1,517
1,509
1,327
947
328
619
5,882
206
5,318
113
424
2,274
1,598
814
454
852
276
756
287
829
136
B-5
-------
TABLE B-7
Atlantic
Bergen
Burlington
Camden
Cape May
Cumberland
Essex
Gloucester
Hudson
Hunterdon
Mercer
Middlesex
Monmouth
Morris
Ocean
Passaic
Salem
Somerset
Sussex
Union
Warren
COMPONENTS
1972
FOREST AREA
(THOUSANDS
OF ACRES)
199
0
288
49
67
125
0
56
0
90
32
47
101
150
260
50
62
60
195
0
99
FOR NATURAL SOURCE EMISSIONS
PERCENT
PINE
TREES
30.9
0
36.0
35.8
27.0
29.4
0
19.5
0
4.5
5.2
6.3
27.5
3.8
38.0
5.0
20.7
5.9
5.2
0
5.3
1974
HARVESTED
FARM LAND
(ACRES)
13,605
1,611
68,585
6,066
6,800
54,748
1,366
43,118
133
56,219
28,668
23,106
47,479
12,914
4,146
279
65,078
24,753
26,555
426
42,539
1974
TOTAL FARM LAND
MINUS HARVESTED
FARM LAND
(ACRES)
3,135
400
10,614
1,323
951
8,338
414
6,127
20
20,975
6,445
2,084
12,567
5,011
1,927
32
11,953
10,216
19,307
57
13,542
B-6
-------
TABLE B-8
NUMBER OF HOSPITAL EMPLOYEES1 IN NEW JERSEY 1976
Atlantic 0
Bergen 6,796
Cape May 25
Cumberland 100
Essex 12,712
Hudson 6,623
Hunterdon 750
Middlesex 1,119
Monmouth 4,977
Morris 4,604
Ocean 0
Passaic 4,959
Somerset 3,004
Sussex 762
Union 6,027
Warren 750
1 See Chapter X.
B-7
-------
TABLE B-9
Atlantic
Bergen
Essex
Monmouth
Ocean
1975 OPEN BURNING IN NEW
N.A.F.E.C.
Bergen County Fire School
Teterboro Airport
Newark Airport
Monmouth County Fire Training
USN Sea Lift Command
Lakehurst NAS
JERSEY
JP-4
Gasoline
#2 Fuel Oil
JP-4
JP-4
#2 Fuel Oil
#2 Fuel Oil
Gasoline
JP-4
20,000
1,000
4,000
500
32,000
1,500
12,000
1,920
8,500
TABLE B-10
Atlantic
Cape May
Cumberland
Hunterdon
Ocean
Sussex
Warren
State Total
RAILROAD FUEL USAGE
TRACK
(MI.)
72
60
94
1,687
IN NEW JERSEY
1975 RAILROAD
FUEL USAGE
(103 GAL)
9.6 x 101
7.2 x 101
1.42 x 102
2.0 x 103
1.22 x 102
1.69 x 103
2.63 x 103
4.7 x 104
B-8
-------
TABLE B-ll
1975 ESTIMATE OF AIRPORT AIRCRAFT MIX AND OPERATIONS IN NEW
JERSEY
COUNTY/
AIRPORT
Atlantic
Bader Field
Hammonton
Ocean City
Smithville
Vineland
Nordheim
N.A.F.E.C.
Cape May
Cape May
Woodbine
USCGS Cape May
Cumberland
Bucks
Millville
LiCalzi
Krollinger
Hunterdon
Sky Manor
Cumulus Ridge
Alexandria
Ocean
Lakewood
Manahawkin
Miller
Eagles Nest
NAS Lakehurst
Sussex
Sussex
Aeroflex
Newton
Trinca
Warren
Blairs town
Hackettstown
SINGLE
ENGINE
PISTON
36
47
11
15
16
+1
14. 5%2
30
20
0
+1
56
6
4!
33
2
33
37
6
74
+1
10%6/
5%
63
23
11
26
40
42
MULTI-
ENGINE
PISTON
5
4
3
1
0
0
10%
2
0
0
0
14
0
0
3
0
3
5
0
1
0
90%7/
80%
1
4
0
0
5
0
MULTI-
ENGINE
TURBO
3
0
0
0
0
0
20. 5%3
0
0
0
0
1
0
0
0
0
0
0
0
1
0
0 .
0
0
0
0
0
0
MULTI-
ENGINE
TURBINE
0
0
0
0
0
0
55%4
0
0
0
0
2
0
0
0
0
0
0
0
1
0
0
0
0
0
0
0
0
OTHER
0
0
0
0
0
0
0
0
0
+5
0
I10
0
0
0
0
0
0
0
0
0
15%8
0
0
0
0
2210
0
NUMBER
OF
OPERATIONS
48,750
49,750
12,000
16,250
8,500
5,600
108,875
47,750
11,875
1,505
17,000
52,750
5,375
4,500
26,375
1,000
6,200
30,750
6,875
65,000
2,250
53,6769
46,500
7,000
7,000
7,000
46,375
10,000
Footnotes are on following page.
B-9
-------
TABLE B-ll (CONT.)
AIRPORT AIRCRAFT MIX AND OPERATIONS IN NEW JERSEY
•*- Unknown number, but all single engine piston aircraft.
f\
*• Unknown number, but 14.5% of all operations single engine piston aircraft.
o
J Of the total operations 20% are twin engine turboprop and .5% are four engine
turboprop aircraft.
^ This is composed of 10% jumbo jet, 20% long range jet, and 25% medium range
jet operations.
5 Unknown number, but all helicopters.
° 10% single engine piston and 5% single engine piston military.
' 90% twin engine piston and 80% twin engine piston military.
8 15% single jet engine military.
' 211 of these operations are civil operations.
10 Not considered part of powered aircraft mix because type of aircraft unknown.
B-10
-------
TABLE B-12
VESSELS
See Tables XIV-2 and XIV-3.
TABLE B-13
GENERAL UTILITY FUEL1
GASOLINE
(103 GAL)
Atlantic
Cape May
Cumberland
Hunterdon
Ocean
Sussex
Warner
2,443
940
1,716
1,020
3,819
1,287
1,040
1 Chapter XV, OFF-HIGHWAY VEHICLES,
B-ll
-------
TABLE B-14
NUMBER OF TRACTORS AND FUEL USAGE1
Atlantic
Cape May
Cumberland
Hunterdon
Ocean
Sussex
Warner
State Total
TRACTORS
1974
1,005
222
2,018
1,977
236
948
1,338
18,883
DIESEL FUEL
(103 GAL)
172
38
345
338
40
162
229
3,225
GASOLINE
(103 GAL)
257
57
517
507
60
243
343
*~
Chapter XV, OFF-HIGHWAY VEHICLES,
TABLE B-15
1975 FUEL USAGE FOR DIESEL CONSTRUCTION EQUIPMENT
Atlantic
Cape May
Cumberland
Hunterdon
Ocean
Sussex
Warren
State Total
PERCENT
CONSTRUCTION
EMPLOYMENT
2.7
1.5
1.5
.9
3.4
.7
.8
100.0
DIESEL FUEL
(103 GAL)
33.8
18.8
18.8
11.3
42.5
87.5
100.0
1,250.0
Chapter XV, OFF-HIGHWAY VEHICLES.
B-12
-------
TABLE B-16
NUMBER OF HOUSING UNITS FOR 1975
Hunterdon
Sussex
Warren
TOTAL
DWELLING
UNITS
22,110
24,420
24,550
1 UNIT
PER
STRUCTURE
18,290
21,500
18,900
2 UNITS
PER
STRUCTURE
2,140
1,420
2,960
3-4 UNITS
PER
STRUCTURE
750
710
840
5-19 UNITS
PER
STRUCTURE
690
610
1,270
20+ UNITS
PER
STRUCTURE
240
180
580
1 For Chapter XVI, RESIDENTIAL HEATING FUEL.
TABLE B-17
RESIDENTIAL METHODS OF SPACE HEATING FOR 1975
(PERCENT)
NATURAL
GAS
LPG
ELECTRIC
OIL
COAL
WOOD
OTHER
Hunterdon
Sussex
Warren
6.74
3.93
6.54
2.25
3.28
1.15
7.27
5.95
4.79
80.54
83.53
73.02
2.44
2.44
4.13
.47
.36
.18
.28
.51
.19
B-13
-------
TABLE B-18
NEW JERSEY POPULTION1
1970
Hunterdon
Sussex
Warren
69,718
77,528
73,879
For Chapter XVI, Residential Heating Fuel.
TABLE B-19
RESIDENTIAL FUEL USAGE IN
Atlantic
1974
1980
1985
1990
Cape May
1974
1980
1985
1990
Cumberland
1974
1980
1985
1990
Ocean
1974
1980
1985
1990
COAL
(TONS)
850
0
0
0
50
0
0
0
1,460
0
0
0
0
0
0
0
DISTILLATE
OIL
(103 GAL)
30
33
36
38
13
15
19
22
37
41
45
50
35
49
62
76
,335
,560
,180
,620
,093
,990
,190
,390
,926
,980
,860
,380
,582
,120
,360
,550
NEW JERSEY
RESIDUAL NATURAL
OIL GAS
(103 GAL) (MCF)
200
221
239
255
0
0
0
0
500
553
605
664
0
0
0
0
3.0
3.1
3.0
3.1
1.4
1.6
1.4
1.6
1.4
1.5
1.4
1.5
6.2
6.3
6.2
6.3
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
106
10 6
10 6
10 6
106
10 6
10 6
10 6
106
10 6
10 6
10 6
106
10 6
10 6
10 6
L.P.G.
(103 GAL)
8.72
8.72
8.72
8.72
24.76
24.76
24.76
24.76
8.87
8.87
8.87
8.87
16.12
16.12
16.12
16.12
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
X
102
102
102
102
102
102
102
102
102
102
102
102
102
102
102
102
WOOD
(TONS)
205
225
242
257
466
554
652
750
344
389
435
488
213
271
328
389
B-14
-------
TABLE B-20
1975 COMMERCIAL FUEL USAGE IN NEW JERSEY
Hunterdon
Sussex
Warren
Commercial
Residential
State Total
WHOLESALE
AND RETAIL
EMPLOYMENT
(PERCENT)
.85
.72
.86
Total
Total
100
DISTILLATE
OIL
(103 GAL)
7,413
6,279
7,500
872,200
933,790
1,806,000
TABLE B-21
COMMERCIAL FUEL USAGE IN
Atlantic
1974
1980
1985
1990
Cape May
1974
1980
1985
1990
Cumberland
1974
1980
1985
1990
Ocean
1974
1980
1985
1990
COAL
(TONS)
150
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
DISTILLATE
OIL
(103 GAL)
10,687
14,430
17,170
20,310
2,371
3,310
4,030
4,860
15,924
20,970
24,890
29,590
6,512
9,380
11,550
14,080
RESIDUAL
OIL
(103 GAL)
3,469
2,939
3,510
408,170
9,430
417,600
NEW JERSEY
RESIDUAL
OIL
(103 GAL)
2,766
3,730
4,440
5,260
1,317
1,840
2,240
2,700
9,316
12,270
14,560
17,310
0
0
0
0
NATURAL
GAS
(106 ft3)
443
375
448
52,147
—
52,147
NATURAL
GAS
(106 ft3)
2,300
2,300
2,300
2,300
570
570
570
570
1,491
1,491
1,491
1,491
1,173
1,173
1,173
1,173
B-15
-------
TABLE B-22
1975 LIGHT INDUSTRIAL FUEL USAGE1 IN NEW JERSEY
MANUFACTURING
EMPLOYMENT
(PERCENT)
Hunterdon .700
Total
Point
Sources
Net
Sussex
Total .315
Point
Sources
Net
Warren 1.387
Total
Point
Sources
Net
State 100.
Total
Residential
Net
DISTILLATE
OIL
(103 GAL)
685
- 5,705
0
308
954
0
1,357
770
587
97,818
0
97,818
RESIDUAL
OIL
(103 GAL)
1,768
- 3,637
0
796
0
796
3,503
- 8,076
0
252,546
0
252,546
ANTHRACITE
COAL
(TONS)
323
0
323
145
0
145
640
0
640
129,119
- 82,980
46,139
BITUMINOUS
COAL
(TONS)
266
0
266
120
0
120
527
0
527
38,000
0
38,000
NATURAL
GAS
(106 FT3)
367
0
367
165
0
165
726
9,009
0
52,361
0
52,361
The point source inventory does not include every user of fuel and the
"Natural Industry Survey" does not include all the fuel used in a state.
In addition, any method of allocating state fuel totals to the county
level will over estimate the fuel quantities in some counties and under
estimate them in others.
B-16
-------
TABLE B-23
LIGHT INDUSTRIAL FUEL USAGE IN NEW JERSEY
DISTILLATE OIL
(103 gal)
RESIDUAL OIL
(103 gal)
NATURAL GAS
(106 ft3)
Atlantic
1974
1980
1985
1990
Cape May
1974
1980
1985
1990
Cumberland
1974
1980
1985
1990
Ocean
1974
1980
1985
1990
0
14
27
41
349
445
515
616
7,732
10,370
12,350
14,640
1,795
2,870
3,820
4,880
0
0
0
0
0
0
0
0
11,653
15,620
18,610
22,060
0
0
0
0
9
9
9
9
38
38
38
38
920
920
920
920
742
742
742
742
R-i 7
-------
TECHNICAL REPORT DATA
(Please read Instructions on the reverse before completing)
1. REPORT NO.
EPA 902/4-79-001
3. RECIPIENT'S ACCESSION NO.
4. TITLE AND SUBTITLE
New Jersey Area Source VOC and No
Emissions
5. REPORT DATE
March 1979
Inventory (for Selected Counties and Categories)
6. PERFORMING ORGANIZATION CODE
7. AUTHOR(S)
8. PERFORMING ORGANIZATION REPORT NO.
9. PERFORMING ORGANIZATION NAME AND ADDRESS
Engineering-Science, Inc.
7903 Westpark Drive
McLean, Virginia 22102
10. PROGRAM ELEMENT NO.
11. CONTRACT/GRANT NO.
68-02-2537
12. SPONSORING AGENCY NAME AND ADDRESS
United States Environmental Protection Agency
Region II, Air Branch
26 Federal Plaza
New York. New York 10009
13. TYPE OF REPORT AND PERIOD COVERED
FINAL
14. SPONSORING AGENCY CODE
15. SUPPLEMENTARY NOTES
16. ABSTRACT
Engineering-Science assisted the New Jersey Department of- Environmental
Protection in the development of the Air Pollution area source emission
inventories for certain categories and counties not previously evaluated. The
base year of this study was 1975 and projections were made for 1977, 1982, and
1987. Included among the nineteen categories, which were inventoried for
volatile organic compounds and oxides of nitrogen, were pesticide application
and natural source emissions. The oxidant season, April 1 extending through
September 30, proportion of annual emissions were accessed for all nineteen
categories, the base year, and projection years.
17.
KEY WORDS AND DOCUMENT ANALYSIS
DESCRIPTORS
b-IDENTIFIERS/OPEN ENDED TERMS C. COSATI Field/Group
Air Pollution
State of Jew Jersey
Emission inventory
Volatile Organic
Compounds and Oxides of
Nitrogen
18. DISTRIBUTION STATEMENT
Release Unlimited
19. SECURITY CLASS (This Report)
Unclassified
21. NO. OF PAGES
130
20. SECURITY CLASS (This page)
Unclassified
22. PRICE
EPA Form 2220—1 (Rev. 4—77) PREVIOUS EDITION is OBSOLETE
------- |