STATEWIDE INVENTORY
OF
AIR POLLUTANT EMISSIONS
STATE OF KANSAS
1970
(Revised)
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PEDCo - ENVI RO N M ENTAL
SUITE e . ATKINSON SQUARE
CINCINNATI. OHIO 45246
513/771-4330
,~
I
STATEWIDE INVENTORY
OF
AIR POLLUTANT EMISSIONS
STATE OF KANSAS
1970
(Revised)
Prepared for:
The Environmental Protection Agency
Durham, North Carolina 27701
Authorization:
Contract Number: 68-02-0044
Task Order No.4
Report Number: PEDCO-72-2
Prepared by:
Timothy.W. Devitt
December 31, 1971
(Initial Draft Issued
August 31, 1971)
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1.0
2.0
3.0
4.0
5.0
6.0
TABLE OF CONTENTS
Page Number
INTRODUCTION
.. ................ ........
1
AREA DESCRIPTION ....... ....... ........
EMISSIONS ESTIMATING PROCEDURES .......
3.1
3.2
3.3
Point Sources ....................
Area Sources - Fuel Combustion ...
Area Sources
- General...........
AREA GRIDDING
4.1
4.2
4.3
4.4
4.5
......... .......... ......
Sedgwick
Coun ty ..................
Shawnee County...................
Leavenworth and Johnson Counties.
Wyandotte
Area Maps
County. . . . . . . . . . . . . . . . .
........ .......... ......
EMISSIONS INVENTORY DATA ..............
5.1
5.2
AQCR Emission Summary Tables
AQCR Emission Summary Graphs
.....
.....
6.1
APPENDICES. . . . . . . . . . . . . . . . . . . . . . . . . . . .
6.2
Appendix A - Fuel Combustion
Emission Factors .................
Appendix B - Source Emission
Reports, Kansas State Department
of Hea 1 th ........................
2
6
6
7
18
31
31
33
34
34
34
44
46
67
74
74
76
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1.0
INTRODUCTION
This report presents the results of the air pollutant
emissions inventory of the State of Kansas.
The purposes of
the study were:
1.
To calculate the 1970 quantity of air pollutants
emitted from point and area sources in the State
of Kansas.
2.
To assemble the emission data in a suitable format
for use in developing the Implementation Plan.
The five pollutants included in the emissions inventory
are particulates, sulfur dioxide, nitrogen dioxide, carbon
monoxide, and hydrocarbons.
Point source emission estimates, with the exception of
those for Wyandotte County, were prepared by the Air Quality
and Occupational Health Section of the Environmental Health
Division, Kansas State Department of Health.
Emissions from
point sources in Wyandotte County were calculated by the
Kansas City, Kansas, Wyandotte County Department of Health,
Division of Air Pollution Control.
PEDCo-Environmental
Specialists, Inc. calculated the area source emissions and
assembled the area and point source emission data in the
required implementation plan format.
- 1 -
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2.0
AREA DESCRIPTION
The seven Kansas Air Quality Control Regions and the
counties in each Region are shown in Figure 1.1.
The AQCR
region codes are in parentheses.
The political jurisdiction
codes, which are used to identify individual counties within
each AQCR, are listed in Table 2.1.
Sedgwick and Shawnee Counties and the Kansas portion of
the Kansas City Interstate AQCR were divided into grids of
6.5, 25 and 100 square kilometers.
Maps of these grid
systems are in Section 4.5, Area Maps.
- 2 -
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Northwest Kansas. ::n :ras :a :e
Air Quality Contro:. Region
(097)
North Cen :ral Kansas: :ntra-
state Air Quality Control
Region (096.)
Northeas: Kansas Intra
state Air Quality Contro:.
Region (095)
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Southwest Kansas Intra-
state Air Quality Control
Region (100)
South Central Kansas
Intrastate Air Quality
Control Region (099)
Southeast Kansas Intra-
state Air Quality Control
Region (098)
Figure 1.1
State of Kansas Air Quality Control Regions
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TABLE 2.1 - POLITICAL JURISDICTIONS WITHIN THE
KANSAS AIR QUALITY CONTROL REGIONS
Region No. 094 - Metropolitan Kansas City Interstate Air Quality
Control Region
1.
2.
Johnson County
Leavenworth County
3. Wyandotte County
Region No. 095 - Northeast Kansas Intrastate Air Quality Control
Region
1.
2.
3.
4.
5.
6.
7.
Atchinson County
Brown County
Doniphan County
Douglas County
Franklin County
Jackson County
Jefferson County
8.
9.
10.
11.
12.
13.
14.
Marshall County
Miami County
Nemaha County
Osage County
Pottawatomie County
Shawnee County
Wabaunsee County
Region No. 096 - North Central Kansas Intrastate Air Quality Control
Region
l.
2.
3.
4.
5.
6.
7.
8.
Clay County
Cloud County
Dickinson County
Ellsworth County
Geary County
Jewell County
Lincoln County
McPherson County
9.
10.
ll.
12.
13.
14.
15.
16.
Mitchell County
Morris County
Ottawa County
Republic County
Rice County
Riley County
Saline County
Washington County
Region No. 097 - Northwest Kansas Intrastate Air Quality Control
Region
1.
2.
3.
4.
5.
6.
7 .
8.
9.
10.
11.
Barton County
Cheyenne County
Decatur County
Ellis County
Gove County
Graham County
Logan County
Ness County
Norton County
Osborne County
Phillips County
12.
13.
14.
15.
16.
17.
18.
19.
20.
21.
- 4 -
Rawlins County
Rooks County
Rush County
Russell County
Sheridan County
Sherman County
Smi th County
Thomas County
Trego County
Wallace County
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Region No. 098 - Southeast Kansas Intrastate Air Quality Control
Region
1.
2.
3.
4.
5.
6.
7.
8.
Allen County
Anderson County
Bourbon County
Chautauqua County
Cherokee County
Coffey County
Crawford County
Elk County
9.
10.
11.
12.
13.
14.
15.
16.
Greenwood County
Labette County
Linn County
Lyon County
Montgomery County
Neosho County
Wilson County
Woodson County
I . .
Region No. 099 - South Central Kansas Intrastate Air Quality
Control Region
1. Butler County 6. Kingman County
2. Chase County 7 . Marion County
3. Cowley County 8. Reno County
4. Harper County 9. Sedgwick County
5. Harvey County 10. Sumner County
Region No. 100 - Southwest Kansas Intrastate Air Quality Control
Region
1. Barber County 14. Kiowa County
2. Clark County 15. Lane County
3. Comanche County 16. Meade County
4. Edwards County 17. Morton County
5. Finney County 18. Pawnee County
6. Ford County 19. Pratt County
7. Grant County 20. Scott County
8. Gray County 21. Seward County
9. Greeley County 22. Stafford County
10. Hamilton County 23. Stanton County
11. Haskell County 24. Stevens County
12. Hodgeman County 25. Wichita County
13. Kearney County
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3.0
EMISSIONS ESTIMATING PROCEDURES
This section reviews the procedures used to estimate
emissions and, in the case of area source emissions, apportion
the emissions to the appropriate counties.
Methods of
apportioning emissions to the "gridded areas" are discussed
in Section 4.0.
The emission factors used to calculate emissions resulting
from fuel combustion are listed in Appendix A.
3.1
Point Sources
For purposes of this study, a point source was
defined as any source which emits ten tons per year or more
of any single pollutant.
In addition, most, if not all, of
the processes defined in Appendix C of the Federal Register,
Aprdl 9, 1971, were included as point sources irrespective
of the quantity of pollutants emitted.
The point sources were identified in a previous
survey conducted by the Kansas State Agency.
As part of
that survey, approximately 4,000 questionnaires were mailed
to potential sources.
About 1,500 questionnaires were
returned.
Follow-up contacts by area representatives of
the State Agency insured that all potential point sources
were considered.
Additional contacts were made by the
State Agency as part of this emissions inventory to update
the emission estimates and obtain point source fuel usage data.
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Emissions were calculated by applying emission factors
to the fuel quantities, refuse quantities, and production
rates obtained by questionnaires and plant visits.
The
extent of control on each point source was also determined
by questionnaire or plant visit.
Emissions from all point sources are listed in the
computer printout.
In most cases, such information as
stack parameter values, process weights, coordinates and
operating schedules are missing.
However, the State Agency,
as part of its overall enforcement program, is establishing
a reporting schedule for specific firms and will obtain this
information.
A copy of the general questionnaire which all
sources on a reporting schedule will complete and an example
of the forms tailored for specific industries are included
in Appendix B.
A summary tabulation of the point and area source
emissions in each AQCR is presented in Section 5.0 of
this report.
3.2
Area Sources - Fuel Combustion
Fuel usage data determined in a previous Office of
Air Program's survey and by the Wyandotte County Department
of Health were used for the Kansas portion of the Kansas City
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Interstate AQCR.
These fuel totals were subtracted from
State totals to yield the fuel quantities to be apportioned
to the other six AQCR's.
The fuel consumption categories used in the emissions
inventory were residential, commercial-institutional, and
industrial.
This section outlines the procedures used for
determining the quantity of fuel in each category and the
method of apportioning this quantity to the individual counties.
Where specific data were not available, the following
values were used for the fuel parameters:
Bituminous Coal
% Ash
% Sulfur
Distillate Oil
% Sulfur
Residual Oil
% Sulfur
Natural Gas
% Sulfur
11.3
4.4
.27
1.2
.0001
3.2.1
Residential Fuel
A.
Coal
Data:
o 1960 Census of Housing - Kansas;
o Statistical Abstracts of the U.S., 1969;
o U.S. Bureau of Mines, Distribution'of
Pennsylvania Anthracite for Coal Year
April 1, 1967, to March 31, 1968.
o Air Pollutant Emission Inventory Techniques,
Unpublished Report, E.P.A., OAP, Bierbaum, P.G.
and Gedgaudas, M.J.
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Procedure:
Since the fuel use data in the 1970 Census
of Housing were not available, the 1960 census data were
used.
Residential coal usage for each county, with the
exception of those counties in the Kansas portion of the
Kansas City AQCR, was calculated using the number of degree-
days in Wichita -- assumed representative of the State, the
total number of dwelling units using coal for space heating
in each county, and a factor of .0012 tons of coal burned
per dwelling unit-degree day.
To account for the reduction
in the number of units which use coal for space heating and
to place residential coal usage in reasonable proportion to
the commercial-institutional and industrial usage, the
calculated amount was reduced by 35%.
It was assumed that
the coal is all bituminous since only 1,296 tons of anthracite
are reported to have been shipped to Kansas.
For the Kansas City .AQCR, the estimates of residential
coal usage made by the OAP were used.
B.
Fuel Oil
Data:
o 1960 Census of Housing - Kansas;
o Statistical Abstracts of the U. S., .1969.
Procedure: .
The number of dwelling units in the six
AQCR's which use fuel oil for "cooking fuel" and "water
heating fuel" was multiplied by 250 gallons per year-dwelling
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unit.
To determine the quantity of fuel oil consumed for
space heating, the number of dwelling units using fuel oil
for space heating in the six AQCR's was multiplied by the
number of degree-days in Wichita and the factor 0.18 gallons
per dwelling unit-degree day.
The six AQCR residential fuel
oil total (i.e., cooking, water heating and space heating
fuel) was apportioned to the individual counties using the
ratio of the number of dwelling units which use fuel oil
for space heating in a county to the six Region total of
such dwelling units.
In the Kansas City AQCR, the OAP estimates of fuel
oil consumption were used.
. C.
Natural Gas
Data:
o U.S. Bureau of Mines:
Natural Gas Preprint;
1969 Minerals Yearbook,
o Department of Commerce, 1960 Census of Housing -
Kansas.
Procedure:
The quantity of natural gas delivered to
Kansas consumers for residential use was obtained from the
Minerals Yearbook.
The amount of natural gas consumed for
residential use in the Kansas portion of the Kansas City
Interstate AQCR, determined in the OAP survey, was subtracted
from this value.
The difference was apportioned to each
county outside the Kansas City AQCR using, as the apportioning
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II
,
factor, the ratio of the number of dwelling units which use
natural gas for space heating in each county to the total
number of such units in the six other Regions.
3.2.2
Commercial-Institutional Fuel
A.
Coal
Data:
o U.S. Bureau of Mines, Mr. L. Wester strom,
(703) 557-1350;
o U.S. Bureau of the Census, Census of
Manufacturers: 1963. Fuels and Electric
Energy Consumed in Manufacturing Industries:
1962.
o U.S. Department of Commerce, 1967 Census of
Business-Wholesale Trade, Kansas;
o U.S. Department of Commerce, 1967 Census of
Business-Retail Trade, Kansas;
o Kansas State Board of Agriculture, Population
of Kansas by Counties - 1970.
Procedure:
From the Bureau of Mines, it was determined
that 374,000 tons of coal were shipped to Kansas and Nebraska
during 1970 for "retail" and "all other" use.
These categories
include coal used for industrial, commercial-institutional
and residential purposes, but do not include coal used by
power plants.
Based on the industrial coal distribution
data in the Census of Manufacturers' report, it was assumed
that 54% of the 374,000 tons was shipped to Kansas.
The amount
of commercial-institutional and industrial area source coal
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was determined by subtracting the following from this amount:
the point source industrial and commercial coal usage
identified in the point source survey, the residential coal
as calculated above, and the coal used in the Kansas portion
of the Kansas City Interstate AQCR.
This difference was
divided equally between commercial-institutional and industrial
area source coal usage for lack of any data on the actual
distribution.
Furthermore, since there were no reliable data
available regarding fuel usage by individual counties, the
commercial-institutional coal was apportioned to the counties
using the following factor, per the example in the Emission
Inventory Techniques document:
County Apportioning Factor = [1/3 (~) + 1/3 (~)+ 1/3 (¥)]
where:
A = number of retail establishments in
B = number of retail establishments in
C = number of wholesale establishments
D = number of wholesale establishments
E = county population
F = six Region population
a county
the six Regions
in a county
in the six Regions
B.
Distillate Oil
Data: °U.S. Bureau of Mines, Sales of Fuel Oil and
Kerosene in 1969;
°U.S. Department of Commerce, 1967 Census of
Business-Wholesale Trade, Kansas;
°U.S. Department of Commerce, 1967 Census of
Business-Retail Trade, Kansas;
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o Kansas State Board of Agriculture, Population
of Kansas by Counties - 1970.
Procedure:
The quantities of "kerosene" and"distillate-
type heating oils" sold in Kansas were obtained from the
u.S. Bureau of Mines report.
Distillate fuel oil used
domestically in the Kansas portion of the Kansas City AQCR,
and the amount used by commercial-institutional point sources
throughout Kansas were subtracted from the total to yield
the quantity of area source commercial-institutional fuel.
This difference was apportioned to individual counties using
the factors developed for commercial-institutional coal
apportionment.
C.
Residual Oil
Data:
o U.S. Bureau of Mines, Sales of Fuel Oil
and Kerosene in 1969;
o u.S. Department of Commerce, 1967 Census of
Business-Wholesale Trade, Kansas;
o U.S. Department of Commerce, 1967 Census of
Business-Retail Trade, Kansas;
o Kansas State Board of Agriculture, Population
of Kansas by Counties - 1970.
Procedure:
The quantity of oil listed in t~e Bureau of
Mines report as "Residual-type Heating Oils" and "Residual-
type Fuel Oil for use by the Military" were considered to be
used solely for commercial-institutional fuel combustion.
The amount of commercial-institutional residual oil identified
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in the point source survey, and that used in the Kansas City
AQCR for commercial-institutional purposes, was
subtracted
from this total.
The difference was apportioned to each
county using the factors developed for commercial-institutional
coal apportionment.
In the Kansas City AQCR, the quantity of fuel identified
in the OAP survey was used to estimate emissions.
D.
Natural Gas
Data:
o U.S. Bureau of Mines: 1969 Minerals Yearbook,
Natural Gas;
o U.S. Department of Commerce, 1967 Census of
Business-Wholesale Trade, Kansas;
o U.S. Department of Commerce, 1967 Census of
Business-Retail Trade, Kansas;
o Kansas State Board of Agriculture, Population
of Kansas by Counties - 1970;
o Annual Reports by Natural Gas Companies;
Kansas State Corporation Commission, Topeka,
Kansas.
Procedure:
Natural gas sales data by county and user
category, namely residential, commercial, and industrial,
were obtained from the Kansas State Corporation Commission
for the following companies:
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o Arkansas - Louisiana Gas Company
o Central Kansas Power Company
o The Gas Service Company
o Greeley Gas Company
o Kansas-Nebraska Natural Gas Company
o Northern Natural Gas Company
o The Tri City Gas Company
o Union Gas System Inc.
The residential and commercial gas sales by these
companies accounted for approximately 85% of the residential
and commercial sales reported in the Bureau of Mines Yearbook.
However, the Kansas Corporation Commission data did not
include some of the smaller companies and did not distinguish
between residential and commercial natural gas sales for all
companies.
The Bureau of Mines' numbers were considered to
be more complete and thus were used.
Further, since some of
the counties were not included in the Kansas Corporation,
Commission listing, the commercial and institutional natural
gas was apportioned using the same factors as developed for
coal.
The quantity of natural gas apportioned was the
difference between (1) the sum of the "commercial" and "other
consumer" figures in the Bureau of Mines Yearbook, and
(2) the amount of natural gas consumed by commercial/insti~
tutional establishments in the Kansas portion of. the Kansas
City AQCR plus the amount identified in the point source
survey as consumed by commercial and institutional point
sources throughout the state.
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In the Kansas City AQCR, the quantity of natural gas
identified in the earlier OAP survey was used to estimate
emissions.
3.2.3
Industrial Fuel
A.
Coal
Data:
o U.S. Bureau of Mines, Mr. L. Wester strom,
(703) 557-1350;
o U.S. Bureau of the Census, Census of
Manufacturers: 1963. Fuels and Electric Energy
Consumed in Manufacturing Industries: 1962.
o U.S. Department of Commerce, 1967 Census of
Manufacturers, Kansas.
Procedure:
The method of determining the quantity of
area source coal was described in Section 3.2.2A.
Area
source coal was apportioned to the individual counties using
the ratio of the number of manufacturing employees in a
county to the six Region total of such employees as the
apportioning factor.
In the Kansas City AQCR, the coal usage
.estimates prepared by the earlier OAP survey were used.
B.
Distillate Oil
Data:
o U.S. Bureau of Mines, Sales of Fuel Oil and
Kerosene in 1969;
o U.S. Department of Commerce, 1967 Census of
Manufacturers, Kansas.
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Procedure:
The quantities of distillate oil listed
in the Bureau of Mines report as "industrial use", "oil
company use" and "miscellaneous uses" were categorized as
industrial fuel oil.
The quantities of distillate identified
in the point source survey and in the Kansas portion of the
Kansas City AQCR were subtracted from this total.
The
difference was apportioned to the individual counties using
the factor,s developed for industrial coal apportionment.
C.
Residual Oil
Data:
o U.S. Bureau of Mines, Sales of Fuel Oil and
Kerosene in 1969;
o U.S. Department of Commerce, 1967 Census of
Manufacturers, Kansas.
Procedure:
The quantity of residual oil for industrial
use was obtained from the Bureau of Mines report under the
same usage type classifications listed for distillate oil.
The quantities of industrial residual oil identified in the
point source survey and in the Kansas City AQCR were subtracted
from this total.
The difference was apportioned using the
same factors developed for industrial coal apportionment.
D.
Natural Gas
Data:
o U.S. Bureau of Mines: 1969 Minerals Yearbook,
Na tural Gas;
o U.S. Department of Commerce, 1967 Census of
Manufacturers, Kansas.
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Procedure:
From the Bureau of Mines Yearbook, natural
gas usage figures were obtained for the following industrial
categories:
o "industrial use"
o "lease and plant fuel"
o "pipeline fuel".
In addition, the difference between the Bureau of Mines
total for power plant fuel use and the quantity identified
in the point source survey as used by power plants, was added
to the above three natural gas figures.
This was done simply
to include this gas in the emissions inventory.
From this total, the industrial point source natural gas
and the natural gas used in the Kansas portion of the Kansas
City AQCR were subtracted to determine the six Region total
of area source industrial gas.
This quantity was apportioned
using the factors developed for industrial distillate oil
apportionment.
In the Kansas City AQCR, the industrial gas
usage figures identified in the previous OAP survey were used.
3.3
Area Sources - General
3.3.1
Solid Waste Disposal
Data:
o 1968 National Survey of Community Solid Waste
Management Practices, EPA. Cincinnati, Ohio;
o Acreage of Rangeland Intentionally Burned,
Cooperative Extension Service, R.M. Hyde,
Kansas State University.
- 18 -
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Procedure:
The quantity of refuse generated in each
county was calculated using different solid waste generation
factors for rural and urban counties.
All but Johnson,
Sedgwick, Shawnee and Wyandotte counties were considered
rural.
The rural solid waste generation factor used was
5.5 pounds per capita day or one ton of refuse per capita
per year.
For the four urban counties a factor of two tons
per capita per year was used.
From the National Survey data, the quantity of waste
which was collected was determined as well as its method
of disposal.
Only those land disposal sites identified in
the survey as practicing no open burning were considered
sanitary landfills; both "uncontrolled" and "planned and
limited" burning were treated as 100% open burning dumps.
The percent collected ranged from about 30 to 70 per-
cent.
It was assumed that 100% of the uncollected rural
solid waste was open burned.
The uncollected urban waste
was assumed to be domestic, commercial and industrial waste
handled on-site or at a private site.
The ratio of manufactur-
ing employees to population was used to approtion the un-
collected amount of the urban refuse into two categories:
waste which was burned in domestic incinerators and waste
which was burned in commercial-industrial incinerators.
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The open burning dumps identified in the National Survey
were considered point sources and the regional emission totals
are listed in Tables 5.1 through 5.7 under "Open Burning Dumps -
Point Sources".
Although some of the dumps in the Kansas
portion of the Kansas City InterstateAQCR and other regions
may have ceased open burning in either 1970 or 1971, their
estimated 1970 emissions have been included.
The conical burners in Dodge City (Ford County) and Garden
City (Finney County) are listed in the Section 5 tabulation as
"Incineration ~ Point Sources".
Emissions included in the
"Incineration - Area Sources" are those resulting from domestic,
commercial, and industrial incinerators located in the four
urban counties.
The emissions listed in the category "Open Burning, On
Site - Area Sources" are those from the open burning of the
"uncollected" refuse in the rural counties.
Several counties also practice range-burning of agricul-
tural wastes.
The acreage burned in these counties was
estimated by the Kansas State University Extension Service.
Emissions were calculated using the agricultural open burning
emission factors and assuming that an average of ,700 pounds of
material were burned per acre.
Table 3.1 lists by region and
county the acreage burned and the resulting emissions.
The
emissions are also summarized by Air Quality Control Region and
listed under "Agricultural Burning" in Tables 5.1 through 5.7.
- 20 -
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TABLE 3.1 AIR POLLUTANT EMISSIONS FROM AGRICULTURAL BURNING
AQCR ACREAGE1 TONNAGE EMISSIONS (TONS/YEAR)
REGION COUNTY BURNED BURNED PART. S02 CO HC NO
x
095 Marshall 10,000 3,500 30 175 35 3.5
Osage 5,000 1,750 15 88 18 1.8
Pottawatomie 30,000 10,500 90 525 105 10.5
Wabaunsee 50,000 17,500 150 880 180 18
096 Geary 20,000 7,000 60 350 70 7
Morris 40,000 14,000 120 700 140 .14
Riley 25,000 8,750 75 440 90 9
'"
~ 098 Chautauqua 10,000 3,500 30 175 35 3.5
Coffey 5,000 1,750 15 88 18 1.8
Elk 20,000 7,000 60 350 70 7
Greenwood 70,000 24,500 210 1225 245 24.5
Lyon 40,000 14,000 120 700 140 14
Wilson 5,000 1,750 15 88 18 1.8
Woodson 5,000 1,750 15 88 18 1.8
099 Butler 20,000 700 60 350 70 7
Chase 60,000 21,000 180 1050 210 21
Cowley 5,000 1,750 15 88 18 1.8
(1) Data provided by the Kansas State University Extension Service.
-------
3.3.2
Motor Vehicles
Data:
o Number of Miles and Annual Average Daily
Vehicle Miles of Travel on State Highways
(including city connecting links), Local
Federal-aid Secondary Highways, Local City
Streets, and Local Rural Roads in Kansas by
County for the Year Ending December 31, 1969.
State Highway Commission of Kansas, Topeka, Kansas;
o Topeka and Wichita Functional Classification
Maps: Traffic Count Data, State Highway
Commission of Kansas.
o
Final Draft-Gridded Motor Vehicle Emissions
for Kansas City Air Quality Control Region.
Prepared for the Environmental Protection
Agency, Durham, North Carolina by PEDCo-
Environmental Specialists under Contract No.
68-02-0044, Task Order No.4, December 20,
1971.
Procedure:
The total number of vehicular miles driven
in each county was obtained from the Kansas Highway Commission.
The data are listed by the following categories:
State
Highways, Local City Streets, Secondary Highways (rural and
urban), and Local Rural Roads.
The State highways category
includes the Kansas Turnpike and city connecting links.
It
was assumed that all vehicle miles, except those for state
highways, were driven at an average of 25 miles per hour.
State highway travel was assumed to be at an average of 45
miles per hour.
Emission factors based upon vehicle-miles
driven at 25 MPH and 45 MPH were used to calculate the
emissions in each county.
- 22 -
-------
For Shawnee and Sedgwick Counties, traffic maps were
used to estimate vehicular emissions in each grid using the
traffic count method.
Motor vehicle emissions estimates for the Kansas portion
of the Kansas City AQCR were obtained from the December 20,
1971 PEDCo report.
3.3.3
Motor Vehicles - Diesel
Data:
o Revenue from Sale of Diesel Fuel in Kansas,
Department of Revenue, Motor Fuel Tax Division,
Walter Dunn, Chief (913) 296-2411;
o Total Registration for 1968 by County, Kansas
Motor Vehicle Department.
Procedure:
The Department of Revenue collected
$8,258,379 from a $0.08 per gallon tax on diesel fuel.
The
corresponding 103,230,000 gallons were apportioned to
individual counties using the ratio of the number of trucks
registered in a county to the state total of registered trucks.
3.3.4
Aircraft
Data: 0 1971 Airport Directory, Aircraft Owners
and Pilots Association, Washington, D.C. 20014
Procedure:
All airports in Kansas which had a control
tower or at least a 3,500 foot paved runway were sent a ques-
tionnaire requesting 1970 data on the number of f~ight oper-
ations by type of aircraft.
All but two of the twenty-two
questionnaires were returned.
In the several cases where
there was insufficient information regarding the type of air-
craft, the following assumptions were made to use the FAA
flight classification data:
- 23 -
-------
Type of Operation (1)
Type of Aircraft
Air Carrier
95% is jet powered.
Three engine.
Military - Itinerant
80% jet, 20% piston.
65% two engine, 35% single
engine.
Civil - Itinerant
80% piston, 20% jet.
65% single engine, 35%
multi-engine.
Civil - Local
90% piston, 10% jet.
70% single engine, 30%
multi-engine.
Military - Local
90% jet, 10% piston.
90% multi-engine, 10%
single engine.
(1) FAA Classification
3.3.5
Vessels
Data: °Waterborne Commerce of the United States;
Department of the Army Corps of Engineers,
Par t 2 ( P . 13, 19 6 9) .
Procedure:
A total of 2,807,000 tons of freight
movement is listed for the section of the Missouri River
between Kansas City, Kansas and Omaha, Nebraska.
Using a
factor of 1/100 of a gallon of diesel fuel per ton-mile of
barge movement, it was determined that 28,000 gallons of diesel
fuel were consumed per mile of river.
The resulting emissions
- 24 -
-------
were halved since it was assumed that half of the emissions
would be in Missouri.
Emissions were apportioned to each
county, and grid where appropriate, on the basis of the
length of continuous river front.
3.3.6
Railroad
Data:
o U.S. Bureau of Mines, Sales of Fuel
Oil and Kerosene, 1969;
o U.S. Department of Commerce, City and
County Data Book, 1962.
The amount of fuel oil used by railroads
Procedure:
in Kansas was obtained from the Bureau of Mines Report.
The quantity of fuel used by railroads in the Kansas portion
of the Kansas City AQCR (determined by mUltiplying the amount
of railroad fuel used in the entire Interstate AQCR -
identified in the previous OAP survey - by the ratio of
track miles in the Kansas portion of the AQCR to the total
track miles in the AQCR), .was subtracted from the state
value to determine the six Region totals.
This six Region quantity was apportioned to the counties
in proportion to the ratio of the number of transportation
employees in a county to the six Region total of 'such
employees.
The reasonableness of this apportionment was
confirmed by inspection of the railroad map which indicated
track mileage per county.
- 25 -
-------
In Topeka and Wichita, railroad fuel usage was
apportioned to the grids by assuming that 80% of the fuel
was used equally in those grids with switching yards and
the remaining 20% was used equally in those grids having
railroad tracks but no switching operations.
Railroad emissions estimates developed in the previous
OAP survey of the Kansas City AQCR were used for that region.
3.3.7
Evaporation Loss
Hydrocarbon emissions were calculated for fuel storage
evaporation loss, gasoline marketing, dry cleaning, and
paint and ink solvent loss.
In the computer printout, the
hydrocarbon emissions from all of these sources are listed
by county under the category "solvent evaporation."
In the
region totals, Tables 5.1 through 5.7, fuel storage evapo-
ration losses are listed under "Process Losses, Area Sources"~
losses from gasoline marketing are listed under "Gasoline
Handling"~ and the dry cleaning, paint and ink solvent losses
are listed under, "Miscellaneous-Area Source, Solvent."
A.
Fuel Storage Evaporation Losses
Data:
o Petroleum Facts and Figures, 1967 Edition,
page 160.
o Compilation of Air Pollution Emission
Factors, Preliminary document, April 1971.
- 26 -
-------
Kansas has a total fuel storage capacity
Procedure:
of 125,434,000 and 27,492,000 gallons of gasoline and
kerosene respectively.
The total kerosene capacity was
multiplied by 135/238 to compensate for its lower volatility
and the "corrected kerosene plus gasoline storage capacity
of 140,829,000 gallons was used to calculate emissions.
The emission factors used to calculate the breathing and
working losses for fixed and floating roof tanks are listed
below:
Hydrocarbon Emission Factors for Evaporation
Losses from the Storage of Gasoline
Type of Tank
o Fixed Roof
Breathing Loss
Emission Factor
0.4 lbs per day per
thousand gallons of
storage capacity
Working Loss
11 lbs per thousand
gallons of throughput
o Floating Roof
Breathing Loss
140 lbs per day per
tank
Working Loss
Negligible
Breathing losses from fixed roof storage tanks were
calculated by assuming that 75% of the total fuel storage
capacity is of the fixed roof variety.
- 27 -
-------
Working losses from fixed roof storage tanks were
calculated by assuming that throughput is equal to 6 times
the capacity, as suggested in the Emission Factors document.
Breathing losses for floating roof tanks were calculated
assuming that an "average" tank has a 50 ft. diameter and a
35,000 gallon capacity.
The total fuel storage evaporation losses for the
state are the sum of the above categories.
These emissions
were apportioned using the ratio of gasoline sales in a
specific county to the state total.
B.
Gasoline Marketing
Data:
o Annual Average Daily Vehicle Miles of
Travel in Kansas by County Excluding Travel
on Interstate Highways for the Year Ending
December 31, 1969, and Percent of State
Total, State Highway Commission of Kansas,
Topeka, Kansas;
o Revenue from Sale of Gasoline in Kansas,
Department of Revenue, Motor Fuel Tax
Division, William Dunn, Chief (913) 296-2411.
Procedure:
In 1970, Kansas received $82,298,000 from a
$0.07 per gallon gasoline tax.
This includes $8,440,000
eventually refunded because of "off-road use".
The total
amount of gasoline sold, 1,176 billion gallons, was
apportioned to the counties using the percent of total state
vehicle miles driven in each county as the apportioning
factor.
Evaporation losses from gasoline marketing were
calculated using an emission factor of 21 pounds of hydro-
carbons per thousand gallons of gasoline.
- 28 -
-------
C.
Dry Cleaning
Data:
o 1970 Kansas Population by County, Kansas
State Board of Agriculture.
Procedure:
Dry cleaning solvent evaporation losses
were determined by multiplying the total state population
by the emission factor of 2.7 pounds per capita per year.
Solvent losses for the state were apportioned to each county
on the basis of population.
D.
Paint Solvents
Da ta :
o Chemicals, Petroleum, and Rubber and Plastics
Products Manufacturing; u.S. Department of
Commerce (April 1969).
Procedure:
In 1966, the national value of shipments
of paints and allied products totalled $2,710 million.
The
value of such shipments in Kansas was assumed to be equal to
the state-to-nation ratio of capital expenditures for
chemicals and allied products, namely 14.2/2515.8.
Dollar
apportionment to the counties was on the basis of manu-
facturing employees:
(14.2)
(2515.8) X
(2,710)
(1)
X
# of manufacturing employees (county)
# of manufacturing employees (state)
=
$ millions of dollars (county).
It was further determined that $1 million in paint sales
is equivalent to 450 tons of solvent per year.
This estimate
was based upon:
o A price range of $4 to $7 per gallon.
o 10% to 60% solvent content.
o The fraction of the total sales for the particular
type of paint or allied product considered.
- 29 -
-------
Paint solvent emissions were calculated using the
following formula:
(450)
(1 x lOb)
x $ MilliomDollars (county) = Tons/Yr. Paint
Solvent Emissions.
E.
Ink Solvent Emissions
Data:
o Chemicals, Petroleum, and Rubber and Plastics
Products Manufacturing; U.S. Department of
Commerce, (April 1969).
Procedure:
Total ink sales in the U.S. amounted to
~67 million.
Ink usage was apportioned to the counties
according to the following formula:
(14.2) X (367) X # of manufactur~ng employees (county)
(2515.8) # of manufactur1ng employees (state)
=
$ million ink (county).
Ink solvent emission estimates were based on the
assumptions that ink costs $0.30 per pound and has a
60% volatile content.
The following formula was used:
Ink
Solvent
Emissions
(Tons/Yr.) = ($ Million Ink Sales, County) (.6)
($0.30/lb.) (2,000 lb/ton)
- 30 -
-------
4.0
AREA GRIDDING
Grid systems were prepared for Sedgwick and Shawnee
Counties using the Universal Transverse Mercator System.
The established grid system for Leavenworth, Johnson, and
Wyandotte Counties in the Kansas portion of the Kansas City
Interstate AQCR was used.
All grid systems used 2.5, 5.0 and 10.0 square kilo-
meter grids.
The grid systems extended to the county lines.
4.1
Sedgwick County (Wichita)
The grid apportioning factors for Sedgwick County were
based on the 1970 preliminary population estimates by census
tract and on the data contained in the "1990 Land Use
Projections and Preliminary Development Plan".
This
information was obtained from the Wichita-Sedgwick County
Metropolitan Area Planning Department, Wichita, Kansas.
Residential fuel usage was apportioned to grids using
the ratio of the population in that grid to the county
population.
Commercial-institutional fuel usage was apportioned
using the 1990 land use projection of commercial acreaqe
- 31 -
-------
since the 1960 actual land use data were incomplete.
The
apportioning factor for each grid was the ratio of commer-
cial acreage in that grid to the total commercial acreage
in the county.
Industrial fuel was apportioned to each grid using
the ratio of the 1990 projection of industrial acreage
in that grid to the projected county total of industrial
acreage.
Solvent evaporation emissions were apportioned to
each grid using the ratio of the sum of the commercial-
institutional and industrial acreage in a grid to the
county total of such acreage.
Motor vehicular emissions were determined by the
traffic count method for the 47 grids where traffic data
were available.
This procedure accounted for approximately
85% of the vehicle miles listed as driven in the county by
the Kansas State Highway Commission.
The remaining 15% was
apportioned to the 24 outlying grids by inspection of maps
indicating the miles of highway in each grid.
Diesel
motor vehicle fuel was apportioned using the same factors
developed for gasoline apportionment (e.g., if 1% of the
county total of gasoline powered vehicle miles were driven
in a grid, it was assumed that 1% of the diesel vehicle
miles were also driven in that grid).
- 32 -
-------
4.2
Shawnee County (Topeka)
Apportioning data were obtained from the Topeka Area
Planning Study - Statistics Report, prepared for the Topeka-
Shawnee County Regional Planning Commission, Topeka, Kansas.
Residential and commercial-institutional fuel were
apportioned to individual grids using the ratio of the 1968
population in that grid to the county population.
Open
burning and incineration were apportioned using the same
factors.
Industrial fuel was apportioned using the ratio
of the number of employees in heavy and light industry in
a grid to the county total of such employees.
Solvent
emissions were apportioned on the basis of the ratio of the
number of "heavy and light industry employees" and "all
other employees" in a grid to the county total of such
employees.
Motor vehicle emissions were calculated using the
traffic count method.
Traffic data were available for 22
of the 31 grids.
Approximately 80% of the vehicle miles,
as listed by the Kansas Highway Commission, were accounted
for by this method.
The remaining 20% were apportioned to
the outlying grids by inspection of roadmaps detailing
highway mileage in each grid.
- 33 -
-------
4.3
Leavenworth and Johnson Counties
The ratio of the population in each grid to the county
population was used to apportion the following:
o domestic fuel usage
o commercial-institutional
o open burning
'0 incineration
o solvent evaporation
fuel usage
Industrial fuel usage was apportioned by inspection of
area maps.
Motor vehicle emissions, both gasoline and
diesel, were available from the December 20, 1971 PEDCo
report (see Section 3.3.2).
These are listed in the ~print-
out" as "hand-calculated" emissions.
Also included under
hand calculated emissions are fuel combustion emissions from
railroad and barge operations.
4.4
Wyandotte County
Area source emissions in Wyandotte County were apportioned
to the grids using the same apportioning factors as used in the
previous OAP survey.
4.5
Area Maps
The following figures illustrate the grid systems
and point source locations for Sedgwick and Shawnee Counties:
Figure 4.1 - UTM Grid System for Sedgwick County
Figure 4.2 - UTM Grid System for Shawnee County
Figure 4.3 - UTM Grid System for the Kansas Portion
of the Kansas City Interstate AQCR
- 34 -
-------
Figure 4.4
Location of Point Sources in Sedgwick County
Figure 4.5 - Location of Point Sources in Shawnee County
Figure 4.6 - Location of Point Sources in the Kansas
Portion of the Kansas City Interstate AQCR.
The source numbers on Figures 4.4 through 4.6 are the
individual source numbers used in the computer listing.
Tables 4.1 and 4.2 link the source number to the firm name
for Figures 4.4 and 4.5 respectively.
Because of a con-
fidentiality clause in the enabling ordinance under which
the Division of Air Pollution, Wyandotte County Department of
Health operates, the names of individual point sources were
not released for the majority of the sources in the Kansas
portion of the Kansas City Interstate AQCR.
- 35 -
-------
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FIGURE 4.'1 - UTM GRID SYSTEH 'FOR SEDGE~HCK COUNTY
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FIGURE 4.2 - UTM GRID SYSTEM FOR SHAWNEE COUNTY
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- 38
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615 625 .
?igure 4./ ~oca:ion of
Point Sources Emitting
Over 100 Tons Per Year
in Segwick County
. .
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Figure 4.6
.Location of Point Sources Emitting Over 10~ Tons
Per Year ih the'-Kansas' Portion of the Kansas City
Interstate AQCR. .'
- 41
-------
Table 4.1
POINT SOURCES IN SEDGWICK EMITTING 100 TONS
PER YEAR OF MORE OF ANY POLLUTANT
Source #
3
5
8
20
23
31
32
33
36
42
45
50
51
53
54
56
57
58
64
74
77
Firm
Wichita Flour Mills
Furley Grain
Ross Industries
Vulcan Chemical Co.
McConnell Air Force Base
Grede Foundries
Service Iron Foundry
Ferrolay Foundry
Ehrsam Wichita Foundry
Standard Press Steel
Cargill Inc.
Kansas Gas & Electric
Kansas Gas & Electric
Kansas Gas & Electric
Garvey Grain
SP Wallingford
Ross Industries
Wichita Flour Mills
Ritchie Construction
Derby Refining
Derby Refining
- 42 -
-------
Table 4.2 POINT SOURCES IN SHAWNEE COUNTY EMITTING 100
TONS OR MORE OF ANY POLLUTANT
Source #
Firm
158
159'
173
177
179
185
187
189
Ismert-Hincke
Thompson-Dehydrating
Berry Grain
Topeka Terminal Elevator
Rodney Milling
Goodyear Tire and Rubber
Concrete Material
Kansas Power & Light
- 43 -
-------
5.0
EMISSIONS INVENTORY DATA
Point and area source emissions are summarized by
region in Tables 5.1 through 5.7.
Data in these tables
are based upon information in the point and area source
computer printouts.
Figures 5.1 through 5.7 provide a visual summary
of the major sources of emission in each AQCR.
The pollutant
source categories are the same as those used in Tables 5.1
through 5.7 with the exception of the "Other Mobile" category.
"Other Mobile" includes emissions from all transportation
activities listed in Section IV of Tables 5.1 through 5.7,
except gasoline powered vehicles.
Emissions from gasoline
powered vehciles are shown as a separate category, where
significant.
Note that the category called "commercial"
. includes emissions resulting from commercial, institutional
and industrial fuel combustion.
The computer printouts are bound separately as point
source and area source listings.
Point sources within each
political jurisdiction (i.e. county) are listed alphabetically
for all of the political jurisdictions in each region.
- 44 -
-------
The area source listings contain two types of summaries.
In the first, the "county summary," region totals are
apportioned to the individual counties within the region.
The second type, the "grid summary," is used only for
those counties which were "gridded," namely, Leavenworth,
Johnson, Wyandotte, Sedgwick, and Shawnee.
Here, the
county totals were further apportioned to the individual
grids.
In the area source printout, emissions from several
types of sources are listed under the category "Additional
Emissions."
The following table is the correspondence
between the column number in the printout and the emission
source category.
1
Emission Source Category
Automotive and diesel
emissions if not listed
under the appropriate
computer calculated
column
Column Number
4
Barge traffic
5
Airport operations
6
Railroads if not.1isted
under computer calculated
column
15
Agricultural burning
- 45 -
-------
Table 5.1
EMISSIONS INVENTORY SUMMARY
For the State of Kansas
Kansas Portion of the Kansas City Interstate Air"Quality
Data Representative of Calendar Year 1970
Control Region
"~
, 0'\
Tons of Pollutant/Year Fuel, etc.
~OURCE CATEGORY Part. S02 CO HC NOx Quantity Units
I. FUEL COMBUSTION
A. Residential Fuel-Area Source
1. Coal 84 619 185 44 19 7407 Tons
2. Distillate Oil 23 89 11 7 28 4599 KGAL
3. Natural Gas 225 7 237 95 890 23725 MMCF
4. Wood
5. Other
6. TOTAL 332 715 433 146 937
B. Comm.-Instl. & Industrial
1.a Bituminous Coal-Area Source 5191 7306 741 194 519 87399 Tons
b Bituminous Coal-Pt. Source
2. Coke
3.a Distillate Oil-Area Source 67 174 1 13 269 8945 KGAL
b Distillate Oil-Pt. Source 16 42 0 3 63 238 KGAL
4.a Residual Oil-Area Source 63 517 8 163 5423 KGAL
b Residual Oil-Pt. Source 99 571 0 14 259 8611 KGAL
5.a Natural Gas-Area Source 67 2 40 82 438 7240 MMCF
b Natural Gas-Pt. Source 166 3 31 322 1464 18353 MMCF
6. Process Gas-Pt. Source
7.a Other-Area Source
bOther-Pt. Source
8. TOTAL 5669 8615 813 636 3175
-------
Table 5.1 (cont'd)
EMISSIONS INVENTORY SUMMARY
~
-...J
Tons of Pollutant/Year Fuel, etc.
SOURCE CATEGORY
Part. S02 CO HC NOx . Quantity. Units
C. Steam-Electric Power Plant
1. Anthracite Coal
2. Bituminous Coal 505 17125 133 40 6709 265100 Tons
3. Distillate Oil
4. Residual Oil
5. Natural Gas 58 4 3 277 1949 13874 MMCF
6. Other
7. TOTAL 563 17129 136 317 8658
D. TOTAL FUEL COMBUSTION 6564 26459 1382 1099 12770
II. PROCESS LOSSES
A. Point Sources 20117 660 1303 6623 936
B. Area Sources 1631
III. SOLID WASTE DISPOSAL
A. Incineration
l.a On Site-Area Source 508 109 725 218 218 145005 Tons
1.b On Site-Point Source
B. Open Burning
1. a On Site-Area Source 401 25 2130 752 150 50106 Tons
l.b On Site-Point Source
2.a Dumps-Area Source
2.b Dumps-Point Source 856 37 1411 1201 117 55100 Tons
C. TOTAL SOLID WASTE DISPOSAL 1765 171 4266 2171 485 250211 Tons
IV. TRANSPORTATION-AREA SOURCE
A. Motor Vehicles-Gasoline 622 377 196978 32346 18661 1884960 KVEHMI
Motor Vehicles-Diesel 890 1601 11565 2313 12099 71169 KGAL
B. Off Highway Fuel Usage
-------
Table 5.1 (cont'd)
EMISSIONS INVENTORY SUMMARY
~
co
SOURCE CATEGORY Tons of Pollutant/Year Fuel, etc.
Part. S02 CO HC NOx Quantity Units
C. Aircraft 469 481 8818 1626 199
D. Railroad 1331 3461 3728 2663 3994 106500 KGAL
E. Vessels 7 48 18 14 20 560 KGAL
P. Gasoline Hnd1g. Evap. Losses 3041
G. Other
H. TOTAL TRANSPORTATION 3319 5968 221107 42003 34973
V. MISCELLANEOUS-AREA SOURCES
A. Agricultural Burning
B. Solvent 2759
C. TOTAL MISCELLANEOUS 2759
VI. GRAND TOTAL
A. AREA SOURCE 9948 14816 225177 47806 37667
B. POINT SOURCE 21817 18442 2881 8480 11497
C. TOTAL 31765 33258 228058 56286 49164
-------
Table 5.2
EMISSIONS INVENTORY SUMMARY
For the State of Kansas
Northeast Intrastate Air Quality Control Region
Data Representative of Calendar Year 1970
~
\0
Tons of POllutant/Year Fuel, etc.
SOURCE CATEGORY Part. S02 CO HC
NOx Quantity Units
I. FUEL COMBUSTION
A. Residential Fuel-Area Source
1. Coal 155 1145 343 82 34 13700 Tons
2. Distillate Oil 47 181 23 14 56 9300 KGAL
3. Natural Gas 141 4 149 60 558 14881 MMCF
4. Wood
5. Other
6. TOTAL 343 1330 515 156 648
B. Comm.-Inst1. & Industrial
1. a Bituminous Coal-Area Source 442 735 117 29 43 8784 Tons
b Bituminous Coal-Pt. Source
2. Coke
3.a Distillate Oil-Area Source 28 71 6 109 3618 KGAL
b Distillate Oil-Pt. Source 13 25 0 3 51 1690 KGAL
4.a Residual Oil-Area Source 54 453 7 142 4746 KGAL
b Residual Oil-Pt. Source 28 220 0 3 84 2577 KGAL
5.a Natural Gas-Area Source 307 10 9 550 2563 33755 MMCF
b Natural Ga$-Pt. Source 171 5 24 346 1558 19682 MMCF
6. Process Gas-Pt. Source
7.a Other-Area Source .
bOther-Pt. Source
8. TOTAL 1043 1519 150 944 4550
-------
Table 5.2 (cont'd)
EMISSIONS INVENTORY SUMMARY
VI
o
Tons of Pollutant/Year Fuel, etc.
SOURCE CATEGORY
Part. S02 CO HC NOx . Quanti ty . Units
C. Steam-Electric Power Plant
1. Anthracite Coal
2. Bituminous Coal 925 5057 68 21 1231 136743 Tons
3. Distillate Oil 8 12 0 1 23 864 KGAL
4. Residual Oil 5 84 0 4 63 1180 KGAL
5. Natural Gas 305 10 7 719 7029 35904 MMCF
6. Other
7. TOTAL 1243 5163 75 745 8346
D. TOTAL FUEL COMBUSTION 2629 8012 740 1845 13544
II. PROCESS LOSSES
A. Point Sources 14970 0 3 45 25
B. Area Sources 2271
III. SOLID WASTE DISPOSAL
A. Incineration
1.a On Site-Area Source 516 110 737 221 221 147300 Tons
1.b On Site-Point Source 11 0 11 2 0 1910 Tons
B. Open Burning
1.a On Site-Area Source 989 62 5253 1854 371 123595 Tons
1.b On Site-Point Source .
2.a Dumps-Area Source
2.b Dumps-Point Source 951 61 5040 1780 355 118829 Tons
C. TOTAL SOLID WASTE DISPOSAL 2467 233 11041 3857 947 272805 Tons
IV. TRANSPORTATION-AREA SOURCE
A. Motor Vehicles-Gasoline 693 420 153330 28474 23608 2098901 KVEHMI
Motor Vehicles-Diesel 188 339 2446 489 2559 15053 KGAL
B. Off Highway Fuel Usage
-------
Table 5.2 (cont'd)
EMISSIONS INVENTORY SUMMARY
l11
......
SOURCE CATEGORY Tons of Pollutant/Year Fuel, etc.
Part. S02 CO HC NOx - Quantity Units
C. Aircraft 579 179 7163 1907 231
D. Railroad 211 548 591 422 633 16874 KGAL
E. Vessels
P. Gasoline Hnd1g. Evap. Losses 1962
G. Other
H. TOTAL TRANSPORTATION 1671 - 1485 163530 33254 27031
V. MISCELLANEOUS-AREA SOURCES
A. Agricultural Burning 285 1668 303 31
B. Solvent 1616
C. TOTAL MISCELLANEOUS 285 1668 1919 31
VI. GRAND TOTAL
A. AREA SOURCE 4635 4256 171829 40267 31159
B. POINT SOURCE 17387 5474 5153 2924 10419
C. TOTAL 22022 9730 176982 43191 41578
-------
Table 5.3
EMISSIONS INVENTORY SUMMARY
For the State of Kansas
North Central Intrastate Air Quality Control Region
Data Representative of Calendar Year 1970
01
t\)
Tons of POllutant/Year Fuel, etc.
SOURCE CATEGORY Quan ti ty I Units
Part. 502 CO HC NOx
"
I. FUEL COMBUSTION
A. Residential Fuel-Area Source
1. Coal 79 583 174 42 17 6970 Tons
2. Distillate Oil 27 104 13 8 32 5369 KGAL
3. Natural Gas 117 4 123 49 462 12315 MMCF
4. Wood
5. Other
6. TOTAL 223 691 310 99 511
B. Comm.-Instl. & Industrial
l.a Bituminous Coal-Area Source 226 474 106 26 22 5673 Tons
b Bituminous Coal-Pt. Source 0 0 0 0 0 4 Tons
2. Coke
3.a Distillate Oil-Area Source 23 59 0 4 90 3020 KGAL
b Distillate Oil-Pt. Source 2 3 0 0 8 248 KGAL
4.a Residual Oil-Area Source 19 156 0 2 49 1626 KGAL
b Residual Oil-Pt. Source 0 6 0 0 2 85 KGAL
5.a Natural Gas-Area Source 195 6 76 308 1496 21262 MMCF
b Natural Gas-Pt. Source 119 4 2 265 1175 13287 MMCF
6. Process Gas-Pt. Source
7.a Other-Area Source
bOther-Pt. Source 59 1 0 93 662
8. TOTAL 643 709 184 698 3504
-------
Table 5.3 (cont'd)
EMISSIONS INVENTORY SUMMARY
U1
!.oJ
Tons of Pollutant/Year Fuel, etc.
SOURCE CATEGORY
Part. S02 CO HC NOx . Quantity. Units
c. Steam-Electric Power Plant
1. Anthracite Coal
2. Bituminous Coal
3. Distillate Oil 6 11 0 0 24 897 KGAL
4. Residual Oil 5 v 54 0 2 25 648 KGAL
5. Natural Gas 35 2 0 85 775 4438 MMCF
6. Other
7. TOTAL 46 67 0 87 824
D. TOTAL FUEL COMBUSTION 912 1467 494 884 4839
II. PROCESS LOSSES
A. Point Sources 18393 6422 7 1836 243
B. Area Sources 2004
III. SOLID WASTE DISPOSAL
A. Incineration
l.a On Site-Area Source !
l.b On Site-Point Source r
B. Open Burning !
l.a On Site-Area Source 1170 73 6098 2193 438 146216 Tons
l.b On Site-Point Source
2.a Dumps-Area Source
2.b Dumps-Point Source 532 33 2943 998 200 66525 Tons
c. TOTAL SOLID WASTE DISPOSAL 1702 106 9041 3191 638
IV. TRANSPORTATION-AREA SOURCE I
A. Motor Vehicles-Gasoline 520 315 111507 20962 17873 1575400 KVEHMI I
Motor Vehicles-Diesel 176 317' 2289 458 2394 14085 KGAL I
B. Off Highway Fuel Usage
-------
Table 5.3 (cont'd)
EMISSIONS INVENTORY SUMMARY
VI
~
SOURCE CATEGORY Tons of Pollutant/Year Fuel, etc.
Part. S02 CO HC NOx Quantity Units
C. Aircraft 297 90 3538 965 119
D. Railroad 107 278 299 213 320 8539 KGAL
E. Vessels
F. Gasoline Hndlg. Evap. Losses 1405
G. Other
H. TOTAL TRANSPORTATION 1100 1000 117633 24003 20706
V. MISCELLANEOUS-AREA SOURCES
A. Agricultural Burning 255 0 1490 300 30
B. Solvent 711
C. TOTAL MISCELLANEOUS 255 0 1490 1011 30
VI. GRAND TOTAL
A. AREA SOURCE 3211 2459 125713 29650 23342
B. POINT SOURCE 19151 6536 2952 3279 3114
C. TOTAL > 22362 8995 128665 32929 26456
-------
Table 5.4
EMISSIONS INVENTORY SUMMARY
For the State of Kansas
Northwest Intrastate Air Quality Control Region
Data Representative of Calendar Year 1970
U1
U1
Tons of Pollutant/Year Fuel, etc.
SOURCE CATEGORY Part. S02 CO HC NOx Quantity Units
I. FUEL COMBUSTION
A. Residential Fuel-Area Source
1. Coal 45 334 100 24 10 4000 Tons
2. Distillate Oil 17 67 9 5 21 3441 KGAL
3. Natural Gas 77 2 81 32 303 8093 MMCF
4. Wood
5. Other
6. TOTAL 139 403 190 61 334
B. Comm.-Inst1. & Industrial
l.a Bituminous Coal-Area Source 141 347 92 22 13 4153 Tons
b Bituminous Coal-Pt. Source
2. Coke
3.a Distillate Oil-Area Source 19 48 0 4 73 2505 KGAL
b Distillate Oil-Pt. Source 0 0 0 0 0 12 KGAL
4.a Residual Oil-Area Source 7 54 0 1 17 572 KGAL
b Residual Oil-Pt. Source 4 28 0 1 10 346 KGAL
5.a Natural Gas-Area Source 153 5 65 232 1140 16639 MMCF
b Natural Gas-Pt. Source 19 0 0 46 231 2379 MMCF
6. Process Gas-Pt. Source
7.a Other-Area Source
bOther-Pt. Source 60 1 0 87 665
8. TOTAL 403 483 157 393 2149
-------
Table 5.4 (cont'd)
EMISSIONS INVENTORY SUMMARY
\J1
m
Tons of POllutant/Year Fuel, . etc.
SOURCE CATEGORY
Part. S02 CO HC NOx . Quantity. Units !
C. Stearn-Electric Power Plant I
1. Anthracite Coal
2. Bituminous Coal
3. Distillate Oil 34 .57 0 7 132 4501 KGAL
4. Residual Oil 2 47 0 1 30 586 KGAL
5. Natural Gas 123 4 2 325 3050 16299 MMCF
6. Other
7. TOTAL 159 108 2 333 3212
D. TOTAL FUEL COMBUSTION 701 994 349 787 5695
.,
II. PROCESS LOSSES
A. Point Sources 2563 0 4 2 0
B. Area Sources 1594
!
1111. .
SOLID WASTE DISPOSAL
A. Incineration
1.a On Site-Area Source
1.b On Site-Point Source
B. Open Burning ~
1.a On Site-Area Source 602 38 3197 1128 226 75227 Tons
1.b On Site-Point Source
2.a Dumps-Area .Source
2.b Dumps-Point Source 718 45 3819 1348 269 89862 Tons
C. TOTAL SOLID WASTE DISPOSAL 1320 83 7016 2476 495
IV. TRANSPORTATION-AREA SOURCE
A. Motor Vehicles-Gasoline 415 251 83740 16465 14347 1157500 KVEHMI
Motor Vehicles-Diesel 180 325 2346 469 2455 14439 KGAL
B. Off Highway Fuel Usage
-------
Table 5.4 (cont'd)
EMISSIONS INVENTORY SUMMARY
U1
-..J
SOURCE CATEGORY Tons of Pollutant/Year Fuel, etc.
Part. S02 CO HC NOx Quantity Units
C. Aircraft 18 3 6 9 15
D. Railroad 69 180 194 139 208 5550 KGAL
E. Vessels
F. Gasoline Hndlg. Evap. Losses 987
G. Other
H. TOTAL TRANSPORTATION 682 759 86286 18069 17025
V. MISCELLANEOUS-AREA SOURCES
A. Agricultural Burning
B. Solvent 416
C. TOTAL MISCELLANEOUS 416
VI. GRAND TOTAL
A. AREA SOURCE 1743 1654 89830 21527 18828
B. POINT SOURCE 3523 182 3825 1817 4387
C. TOTAL > 5266 1836 93655 23344 23215
-------
Table 5.5
EMISSIONS INVENTORY SUMMARY
For the State of Kansas
Southeast Intrastate Air Quality Control Region
Data Representative of Calendar Year 1970
VI
co
Tons of Pollutant/Year Fuel, etc.
SOURCE CATEGORY
Part. S02 CO HC NOx Quantity Units
I. FUEL COMBUSTION
A. Residential Fuel-Area Source
1. Coal 314 2325 695 167 70 27806 Tons
2. Distillate Oil 15 58 7 4 18 2971 KGAL
3. Natural Gas 125 4 131 53 492 13132 MMCF
4. Wood
5. Other
6. TOTAL 454 2387 833 224 580
B. Comm.-Inst1. & Industrial
1.a Bituminous Coal-Area Source 392 623 90 23 39 7449 Tons
b Bituminous Coal-Pt. Source 394 318 6 1 81 5400 Tons
2. Coke
3.a Distillate Oil-Area Source 21 56 0 1 86 2859 KGAL
b Distillate Oil-Pt. Source 2 0 0 0 6 227 KGAL
4.a Residual Oil-Area Source 51 425 0 7 134 4462 KGAL
b Residual Oil-Pt. Source 30 215 0 4 85 2710 KGAL
5.a Natural Gas-Area Source 190 6 62 322 1529 20866 MMCF
b Natural Ga$-Pt. Source 89 3 1 200 905 9974 MMCF
6. Process Gas-Pt. Source
7.a Other-Area Source
bather-Pt. Source 37 0 0 55 105
8. TOTAL 1206 1646 159 613 2885
-------
Table 5.5 (cont'd)
EMISSIONS INVENTORY SUMMARY
Il.11
\0
Tons of Pollutant/Year Fuel, etc. I
SOURCE CATEGORY
Part. S02 CO HC NOx . Quantity. Units :
C. Steam-Electric Power Plant
1. Anthracite Coal
2. Bituminous Coal 291 1272 11 3 320 21600 Tons
3. Distillate Oil 2 3 0 0 8 271 KGAL
4. Residual Oil 6 82 0 5 78 1506 KGAL
5. Natural Gas 81 3 2 243 2274 11676 MMCF
6. Other 3 0 0 0 0
7. TOTAL 383 1360 13 242 2680 :
,
D. TOTAL FUEL COMBUSTION 2043 5393 1005 1079 6145
II. PROCESS LOSSES
A. Point Sources 76086 0 49 60 60 I
B. Area Sources 2633
I
II. SOLID WASTE DISPOSAL I
A. Incineration
I. a On Site-Area Source
l.b On Site-Point Source
B. Open Burning
1.a On Site-Area Source 891 56 4734 1671 334 111392 Tons
l.b On Site-Point Source
2.a Dumps-Area Source
2.b Dumps-Point Source 964 60 5122 1808 362 120473 Tons
C. TOTAL SOLID WASTE DISPOSAL 1855 116 9856 3497 698
IV. TRANSPORTATION-AREA SOURCE
A. Motor Vehicles-Gasoline 549 333 116652 22023 18954 1665900 KVEHMI
Motor Vehicles-Diesel 171 308 2223 445 2326 13682 KGAL
B. Off Highway Fuel Usage I
-------
Table 5.5 (cont'd)
EMISSIONS INVENTORY SUMMARY
~
o
SOURCE CATEGORY Tons of Pollutant/Year Fuel, etc.
Part. S02 CO HC NOx. Quantity Units
C. Aircraft 22 23 621 91 10
D. Railroad 155 402 433 309 464 12363 KGAL
E. Vessels
P. Gasoline Hnd1g. Evap. Losses 1334
G. Other
H. TOTAL TRANSPORTATION 897 .1066 119929 24202 21754
V. MISCELLANEOUS-AREA SOURCES
A. Agricultural Burning 465 0 2714 544 56
B. Solvent 2242
C. TOTAL MISCELLANEOUS 465 0 2714 2786 56
VI. GRAND TOTAL
A. AREA SOURCE 3361 4619 128362 31869 24512
B. POINT SOURCE 77985 1956 5191 2370 4284
C. TOTAL 81346 6575 133553 34239 28796
-------
Table 5.6
EMIssrONS INVENTORY SUMMARY
For the State of Kansas
South Central Intrastate Air Quality Control Region
Data Representative of Calendar Year 1970
0'\
I-'
Tons of POllutant/Year Fuel, etc.
SOURCE CATEGORY Part. S02 CO
HC NOx Quantity Units
I. FUEL COMBUSTION
A. Residential Fuel-Area Source
1. Coal 50 369 110 26 11 4415 Tons
2. Distillate Oil 20 76 10 6 23 3902 KGAL
3. Natural Gas 124 4 130 52 489 13049 MMCF
4. Wood
5. Other
6. TOTAL 194 449 250 84 523
B. Cornm.-Instl. & Industrial
1. a Bituminous Coal-Area Source 1321 1970 241 62 132 23564 Tons
b Bituminous Coal-Pt. Source
2. Coke
3.a Distillate Oil-Area Source 61 158 1 12 243 8112 KGAL
b Distillate Oil-Pt. Source 33 90 0 7 133 4451 KGAL
4.a Residual Oil-Area Source 442 1534 2 24 482 16079 KGAL
b Residual Oil-Pt. Source 30 208 0 3 80 2684 KGAL
5.a Natural Gas-Area Source 658 22 168 1192 5528 72177 MMCF
b Natural Gas-Pt. Source 212 7 93 323 1592 32084 MMCF
6. Process Gas-Pt. Source
7.a Other-Area Source
bOther-Pt. Source 22 0 0 48 349
8. TOTAL 2779 3989 505 1671 8539
-------
Table 5.6 (cont'd)
EMISSIONS INVENTORY SU~1ARY
~
N
Tons of Pollutant/Year Fuel, etc.
SOURCE CATEGORY
Part. 502 CO HC NOx . Quantity. Units
C. Steam-Electric Power Plant
1. Anthracite Coal
2. Bituminous Coal
3. Distillate Oil 28 70 0 5 109 3649 KGAL
4. Residual Oil 6 125 0 4 82 1581 KGAL
5. Natural Gas 531 21 14 1414 13667 71641 KGAL
6. Other 7 0 0 19 188
7. TOTAL 572 216 14 1442 14046
D. TOTAL FUEL COMBUSTION 3545 4654 769 3197 23108
II. PROCESS LOSSES I
A. Point Sources 15000 993 1128 664 9114
B. Area Sources 4616
III. SOLID WASTE DISPOSAL
A. Incineration
1. a On Site-Area Source 1445 310 2065 619 619 412996 Tons
1.b On Site-Point Source
B. Open Burning
1.a On Site-Area Source 1046 65 5559 1962 392 130810 Tons
1.b On Site-Point Source
2.a Dumps-Area Source
2.b Dumps-Point Source 1186 74 6300 2275 445 149450 Tons
C. TOTAL SOLID WASTE DISPOSAL 3677 449 13924 4856 1456
IV. TRANSPORTATION-AREA SOURCE
A. Motor Vehicles-Gasoline 1040 630 245688 44513 34763 3150000 KVEHMI
Motor Vehicles-Diesel 290 522 3770 754 3944 23200 KGAL
B. Off Highway Fuel Usage :
-------
Table 5.6 (cont'd)
EMISSIONS INVENTORY SUMMARY
0'\
W
SOURCE CATEGORY Tons of Pollutant/Year Fuel, etc.
Part. 502 CO HC NOx. Quantity Units
C. Aircraft 1275 394 12882 3868 537
D. Railroad 253 658 709 506 760 20256 KGAL
E. Vessels
P. Gasoline Hndlg. Evap. Losses 3080
G. Other
H. TOTAL TRANSPORTATION 2858 2204 263049 52720 40004
V. MISCELLANEOUS-AREA SOURCES
A. Agricultural Burning 255 0 1488 298 30
B. Solvent 4596
C. TOTAL MISCELLANEOUS 255 0 1488 4894 30
VI. GRAND TOTAL
A. AREA SOURCE 8280 6712 272573 66185 47953
B. POINT SOURCE 17055 1588 7535 4762 25759
C. TOTAL 25335 8300 280108 70947 73712
-------
Table 5.7
EMISSIONS INVENTORY SUMMARY
For the State of Kansas
Southwest Intrastate Air Quality Control Region
Data Representative of Calendar Year 1970
m
~
Tons of Pollutant/Year Fuel, etc.
SOURCE CATEGORY
Part. S02 CO HC NOx Quantity units
I. FUEL COMBUSTION
A. Residential Fuel-Area Source
1. Coal 24 176 53 13 5 2105 Tons
2. Distillate Oil 25 99 13 8 31 5091 KGAL
3. Natural Gas 74 2 78 31 292 7798 MMCF
4. Wood
5. Other
6. TOTAL 123 277 144 52 328
B. Cornm.-Instl. & Industrial
l.a Bituminous Coal-Area Source 171 366 84 21 16 4377 Tons
b Bituminous Coal-Pt. Source
2. Coke
3.a Distillate Oil-Area Source 18 46 0 3 71 2374 KGAL
b Distillate Oil-Pt. Source 1 1 0 0 3 98 KGAL
4.a Residual Oil-Area Source 13 110 0 2 35 1163 KGAL
b Residual Oil-Pt. Source
S.a Natural Gas-Area Source 163 6 60 264 1268 17807 MMCF
b Natural Gas-Pt. Source 39 0 0 87 378 4316 MMCF
6. Process Gas--pt. Source
7.a Other-Area Source
bOther-Pt. Source 181 7 0 286 1987
8. TOTAL 568 536 144 663 3758
-------
EMISSIONS INVENTORY SUMMARY
Tons of Pollutant/Year Fuel, etc.
SOURCE CATEGORY Part. S02
CO HC NOx . Quantity. Units
C. Steam-Electric Power Plant
1. Anthracite Coal
2. Bituminous Coal
3. Distillate Oil 8 13 0 0 32 1060 KGAL
4. Residual Oil 1 25 0 1 17 319 KGAL
5. Natural Gas 131 4 3 330 2660 16454 MMCF
6. Other !
7. TOTAL 140 42 3 331 2709
~ I
D. TOTAL FUEL COMBUSTION 831 855 291 1046 6795
II. PROCESS LOSSES
A. Point Sources 4952 0 596 10069 8
B. Area Sources l756 !
III. SOLID WASTE DISPOSAL
A. Incineration
l.a On Site-Area Source
l.b On Site-Point Source 359 36 1076 359 90 35880 Tons
B. Open Burning I
l.a On Site-Area Source 724 45 3844 1357 271 90443 Tons
l.b On Site-Point Source
2.a Dumps-Area Source
2.b Dumps-Point Source 784 18 1509 532 107 35426 Tons
C. TOTAL SOLID WASTE DISPOSAL 1867 99 6429 2248 468 90443 Tons
I
,
IV. TRANSPORTATION-AREA SOURCE !
A. Motor Vehicles-Gasoline 522 316 110472 20880 18016 1582300 KVEHMI
Motor Vehicles-Diesel 176 317 2293 459 2398 14108 KGAL
B. Off Highway Fuel Usage
-------
Table 5.7 (cont'd)
EMISSIONS INVENTORY SUMMARY
m
m
SOURCE CATEGORY Tons of Pollutant/Year Fuel, etc.
Part. S02 CO HC NOx Quantity Units
C. Aircraft 35 44 1495 184 13
D. Railroad 82 214 230 165 247 6581 KGAL
E. Vessels
P. Gasoline Hnd1g. Evap. Losses 1418
G. Other
H. TOTAL TRANSPORTATION 815 891 114490 23106 20674
V. MISCELLANEOUS-AREA SOURCES
A. Agricultural Burning
B. Solvent 423
C. TOTAL MISCELLANEOUS - 423
,
VI. GRAND TOTAL
A. AREA SOURCE 2027 1741 118322 26984 22663
B. POINT SOURCE 6456 104 3184 11664 5282
C. TOTAL 8483 1845 121506 38648 27945
-------
)AR-ICULA"" :
SOLI D
WASTE
5.6%
OTHER
MO B LI E
8.5%
COMMERCIAL*
17.9%
0'1
-..J
HYDROCARBON
OTHER
MOBILE
10.6%
OTHER 6.5%
SOLID
WASTE
3.9%
SU-F.R OXIDES
CARBON MONOXIDE
~
OTHER
MO 8 IL E
16.8%
COMMERCIAL*
25.9%
NITROGEN OXIDES
POWER
PLANTS
17.6%
OTHER 5.1%
COMME RC I AL* 6.5%
* FUEL COMBUSTION - INCLUDES COMMERCIAL, INSTITUTIONAL & INDUSTRIAL FUEL
FIGURE 5.1 POLLUTANTS EMITTED BY PRINCIPAL SOURCES - KANSAS PORTION OF THE
f1ETROPOLITAN KANSAS CITY INTERSTATE AIR QUALITY CmITROL REGION
-------
PARTICULA'.::
S.L~UR OXIDES
RESIDENTIAL
13.7%
COMMERCIAL*
15.7%
POWE~ P_Af.S 5.5%
SOLID WASTE 11.2%
'----
OTHER 10.1%
OTHER 6.5%
CARBON MONOXIDE
OTHER
MOBILE
5.8%
OTHER MOBILE 11.1%
(j\
CD
HYDROCARBON
NITROGEN OXIDES
PROCESS 5.4%
WASTE 9.0%
OTHER
13.9%
PLANTS 20.0%
OTHER
MOBILE
11 .0%
OTHER
MOBILE
8.2%
* FUEL COMBUSTION - INCLUDES COMMERCIAL, INSTITUTIONAL & INDUSTRIAL FUEL
FIGURE 5.2 POLLUTANTS EMITTED BY PRINCIPAL SOURCES - NORTHEAST
KANSAS INTRASTATE AIR QUALITY CONTROL REGION
-------
PAR'.,:.LAT::
SU-F.R O.xIDES
SOLID
WASTE
7.6%
OTHER 10.3%
CARBON MONOXIDE
COMt~ERCIAL * 7.9%
OTHER 5.4%
0'1
~
HYDROCARBON
NITROGEN OXIDES
SOLID
WASTE 9.7%
COMMERCIAL *
13.2%
PROCESS 11.7%
OTHER
MOBILE 9.2%
POWER
PLANTS
3.1%
OTHER
MOBILE 10.7~
OTHER 5.5%
* FUEL COMBUSTIO~ - INCLUDES COMMERCIAL, INSTITUTIONAL & INDUSTRIAL FUEL
FIGURE 5,3 POLLUTANTS EMITTED BY PRINCIPAL SOURCES - NORTH CENTRAL
KANSAS INTRASTATE AIR QUALITY CONTROL REGION
-------
PARTICULATE
:OMM:RCIAL* 7.7%
CARBON MONOXIDE
GASOLINE
VEHICLES
7.9%
10.6%
-....J
o
HYDROCARBON
PROCESS 6.9%
SOLID WASTE 10.6%
OTHER MOBILE 6.8%
OTHER 4.9%
Sl_:.R OXIDES
OTHER 18,10
RESIDENTIAL
21.9%
COMMERCIAL*
26.2%
POWER
PLANTS
5.9%
OTHER
MOBILE 2.7%
OTHER 7.8%
NITROGEN OXIDES
COM r~ E R C I A L
9.3%
POWER PLANTS
13.8%
* FUEL COMBUSTION - INCLUDES COMMERCIAL, INSTITUTIONAL & INDUSTRIAL FUEL
FIGURE 5.4 POLLUTANTS EMITTED BY PRINCIPAL SOURCES - NORTHWEST
KANSAS INTRASTATE AIR QUALITY CONTROL REGION
OTHER
MOBILE
11 .5%
OTHER
3.3%
-------
JARTICULAT:
HYDROCARBON
-...J
.......
SlL:UR
pTH:R27.5%
OTHER
MOBILE
11.1%
OXIDES
SOLID WASTE 2.3%
OTHER 4.1%
CARBON MONOXIDE
SOLI D WASTE 7.4%
RESIDENTIAL
36.3%
OTHER MOBILE 2.4%
OTHER 2.8%
NITROGEN OXIDES
PROCESS 7.9%
SOLID WASTE 10.2%
POWER PLANTS
9.3%
OTHER MOBILE6.4%
OTHER
MOBILE
9.7%
OTHER 11.1%
OTHER 4.9~
* FUEL COMBUSTION - INCLUDES COMMERCIAL, INSTITUTIONAL & INDUSTRIAL FUEL
FIGURE 5.5 POLLUTANTS EMITTED BY PRINCIPAL SOURCES - SOUTHEAST
KANSAS INTRASTATE AIR QUALITY CONTROL REGION
-------
)ARTICULA.. :
COMMERCIA_* 1.0%
OTHER 3.3%
RESIDENTIAL 7.7%
GASOLINE VEHICLES
4.1%
SOLI D
WASTE
14.5%
CARBON MONOXIDE
OTHER 1.0%
HHER
OTHER
i"10BILE
18.9%
PROCESS
11 .9%
RESIDENTIAL
5.4%
OXIDES
GASO_INE VEHIC_:S
7.6%
OTHER MOBILE
5.9%
SOLID WASTE 5.0%
I~
I
HYDROCARBON
PROCESS 7.5% SOLID WASTE
6.4%
OTHER MOBI LE 11. 5%
COMMERCIAL* 2.4%
OTHER 9.5%
PROCESS 12.3%
OTHER 2.7%
NITROGEN OXIDES
OTHER
MOBILE
7 .1 %
* FUEL COMBUSTION - INCLUDES COMMERCIAL, INSTITUTIONAL & INDUSTRIAL FUEL
FIGURE 5.6 POLLUTANTS EMITTED BY PRINCIPAL SOURCES - SOUTH
CENTRAL KANSAS INTRASTATE AIR QUALITY CONTROL REGION
-------
OTHER
6.5%
CARBON MONOXIDE
SOLID WASTE 5.3%
OTHER 3.7%
SULFUR OXIDES
GASOLINE VEHICLES
17 . 1 %
JARTICULATE
SOLID WASTE 22.1%
GASOLINE
VEHICLES 6.2%
-...J
LV
HYDROCARBON
OTHER 3.9%
OTHER MOBILE
5.7%
NITROGEN
CO~1ME RC I AL *
13.4%
OXIDES
OTHER 2.9%
OTHER
MOBILE 9.5%
PO\1JER
PLANTS
9.7%
SOLID
WASTE
5.8%
* FUEL COMBUSTION - INCLUDES COMMERCIAL, INSTITUTIONAL & INDUSTRIAL FUEL
FIGURE 5.7 POLLUTANTS EMITTED BY PRINCIPAL SOURCES - SOUTHWEST
KANSAS INTRASTATE AIR QUALITY CONTROL REGION
-------
6.0
APPENDICES
6.1
Appendix A
set numbers and the corresponding
The emission factor
emission factors are listed in Tables 6.1 and 6.2 respectively.
TABLE 6.1 EMISSION FACTOR SET NUMBERS USED IN
COMPUTER CALCULATED EMISSIONS FROM POINT SOURCE
FUEL COMBUSTION
Set
Number
Source Type
01
02
03
04
05
-Bituminous
General Pulverized
Wet Bottom Pulverized
Dry Bottom Pulverized
Cyclone
Stoker (Large com-
mercial and general
industrial)
All other Stokers
Stoker (Domestic
and Commercial)
Handfired
06
07
08
09
10
11
-Anthracite
Pulverized Dry Bottom
Overfeed Stokers
Handfired
Coal Boilers-
>100 x 106
>100 x 106
>100 x 10~
>100 x 10
BTU/Hr.
BTU/Hr.
BTU/Hr.
BTU/Hr.
10-100 x 106
10-100 x 106
<10 x 106
<10 x 106
BTU/Hr.
BTU/Hr.
BTU/Hr
BTU/Hr.
Coal Boilers-
12
13
14
15
-Fuel Oil Boilers-
Power Plant-Residual
Industrial and Commercial--Residual
Industrial and Commercial--Distillate
Domestic--Distillate
-Natural Gas Boilers-
16
17
18
19
20
Power Plant
Industrial
Domestic Commercial
Gas Turbines
Gas Engines
74
-------
TABLE 6.2 EMISSION FACTOR
EMISSION
FACTOR
SET # PARTICULATE S02 CO HYDROCARBON N02 UNITS
1 16.000A 38.000S 1.000 0.300 18.000 Pounds per ton of coal burned
2 13.000A 38.000S 1.000 0.300 30.000 "
3 17.000A 38.000S 1.000 0.300 18.000 "
4 2.000A 38.000S 1.000 3.000 55.000 "
5 13.000A 38.000S 2.000 1. 000 15.000 "
6 5.000A 38.000S 2.000 1.000 15.000 "
7 2.000A 38.000S 10.000 3.000 6.000 "
8 2.000A 38.000S 90.000 20.000 3.000 "
9 17.000A 38.0008 1.000 0.030 18.000 "
10 2.000 38.0008 5.000 0.200 10.000 "
11 1. 000 38.0008 90.000 2.500 3.000 "
12 8.000 159.000S 0.040 5.000 105.000 Pounds per thousand gals. of oil burned
13 23.000 159.0008 0.200 3.000 60.000 "
14 15.000 144.000S 0.200 3.000 60.000 "
-...J
U'1 15 10.000 144.000S 0.500 3.000 12.000 "
16 15.000 0.600 0.400 40.000 390.000 Pounds per million cu. ft. of gas burne"
17 18.000 0.600 0.400 40.000 175.000 "
18 19.000 0.600 20.000 8.000 75.000 "
19 15.000 0.600 0.400 40.000 200.000 "
20 15.000 0.600 0.400 40.000 7300.000 "
A = Ash content of coal in percent.
S = Sulfur content of fuel in percent.
Example:
For a. wet bottom pulverized coal fired boiler burning a 3% sulfur content coal,
114 pounds of 802 (38 x 3) would be emitted per ton of coal burned.
-------
6.2
Appendix B
Table 6.3 is an example of the source emission report
required by the Kansas Department of Health for all sources
on a reporting schedule.
Table 6.4 is an example of the
additional reports required of specified industries.
76
-------
TABLE 6.3
KANSAS STATE DEPARTMENT OF HEALTH
Source Emission Report ~Particulate)
Gerleral Processing
Firm Name (Operator)
Mailing Address
Installa tion Loca tion
Products Manufactured or Handled
Sources of particulate discharges exceeding one pound per hour
, ,
(exduding refuse disposal and indirect heating)
, '
Description of individuai sourc'e operations>:: which emit particulate matter (use
supplemental" sheets as necessary).
1.
[
I;
'.
,2.
3.
':t.
--_._~.
. . ..'
':
-------
. TABLE 6. 3
. "". .-. ,
... "
. -',"
.Nature of all material input into process '(by source number - use supplemental
shee~s as necessary). .
Source No.
'. Material (a)
(b)
(c.}.. .
Phys~cal state
Physical state.
Physical state
; lb /hr
; lb / hr
; lb / hr
Primary Fuels (Direct Heating): .' Typ~
; amount burned/hr
; amount burned/hr
.'"r',',
.. .
-. '. Alternate Fuels (Di~ect Heating): Type'
Primary Control Devices (by. source. num\;>er :.. use supplemental sheets as necessary).
Source No.
Manufacturer.
Type'
CFM
.. Model
Ipl~t Gas 'Tern'p. ".
o F.
Volume of Gas Handled
. .
lb /hr
Outlet Dust Rate
lb /hr .
Inlet Dust Rate
Collection Efficiency
%
. "
Method of Disposai of Collected Mate'rials .
. .
Secondary Control Devices (by source ~um.ber - use sl.1pplemerital sheet.s as necessary).
Source No.
Manufacturer
Type
Mod~l
Volume of Gas Hanc;lled
CFM Inlet Ga,s Temp.
OF.
Collection Effidency
lb / hr'
0/0
Outlet Dust Rate
Ib/hr
Inlet Dust Rate
M~thod of Disposal of Collected Materials
If Control Devices are wet scrubbers:
gal/min.
Pressure
Water Flow Rate
psi
Method of waste water disposal
If Control Devices are combustion units:
Temperature
OF.
Fuel Type
Hourly Fuel combustion rate
78
-------
p
TABLE 6.3
Indirect Heating Units
(list individual units - use supplemental sheets as necessary)
a.
Unit No.
Heat Media: .Air
Use: Process Heat
Space Heat
Other
---
Steam
Water
b.
c.
Design -- BTU /hr Operating
, Oil Coal
Average amount burned/hr
- Normal operating schedule:
days/year
Oil
BTU /hr
Maximum Heating Capacity:
Primary Fuel: Natural gas
Other (Specify)
'. 1\tax. amount burned/hr
hOlU's/day from ---- to --
Alternate Fuels:. NatUl'al gas
d.
e.
Coal
n~npr" (
-------
TABLE 6.3.
Other Sources of Particulate Emissions
Are there any other sources of particulate' emissions associated with storage,
transfer and/ or transport of materials, or other use. of the premises? .
If yes, describe briefly: .
'.-
This is to certify tl:1at the above inforIriatic)n is .true and complete' to .the best .of my
knowledge. . .
. .
Signa ture
Ti tle
Date
Return completed form to:
Kansas State Department of Health.
Division of Environniental Health.. .
Air Quality and Occupational Health Section
State Office Building
Topeka, Kansas 66612
80
-------
TABLE 6.4 KANSAS STATE DEPARTMENT OF HEALTH
Source Emission Report - Steam Generating Electric Power Plant
Firm Name (Operator)
Mailing Address
Installa tion Loca tion
Fuel Burning Equipment Data
I i
Maximum Rated Capacity Generator I
30iler Year B TV / hr Stea m Output ~ Type(s)':' Burner Rating Control':":":
I Number Installed !UUU1t/hr PSIG 'F Fuel Type(s )':":' (1000 KW) Devices
.
,
I
I
*Indicate as: C (Coal), G (Gas), 0 plus No. (Oil Grade)
**Indicate by number and letter subscript where 'applicable
I Underfeed V Oil Burner: r(rotary)
II Traveling grate or spreader stoker g(gun type)
III Cyclone furnace
IV Pulverized: w(wet bottom}, d(dry bottom),
Hfly ash reinjection)
*J('*H-Hoppers, M-Mechanical, S-Wet Scrubber, P-Precipitator, F-Fabric Filter,
a-Other. (To be described in more detail on page 4).
VI Gas
VII Other (Specify)
From AQR - B (2/71)
81 '
(over)
-------
TABLE 6.4 Fuel Data (Most recent actual 12 mos. use)
Indicate: From
to
Type>:: Sulfur>:: * Ash>:<>:< Heat Content>:<>:< Cons umption per Hour Annual':"::'::
Fuel % Ave. % Ave. B TV per Average MaxImum Cons umption
-
I
I
~~,,(~~Tith (';'~; i---1.,'fr: ~~'-h("r
*>::If unknown, give name and address of fuel supplier
***Indicate as 106 CF (gas), 1000 gallons (oil) or tons (coal)
Were units operated on fuel other than gas except during periods of actual gas curtailment?
Yes
No
Y" yes, indicate unit numbers, annual amount, and type of fuel used during periods other than
~tual curtailment periods.
82
-------
TABLE 6.4 Fuel Data (Estimate for next 12 mos. )
Indicate: From
to
Type>:' Sulfur':":' Ash';":' Heat Content':':;' Cons umption per Hour Ann ual ':' ':' ':'
Fuel % Ave. % Ave. BTU per Average Maximum Consumption
-
>:
-------
TABLE 6.4 Emission and PolluUqn Control Data
Primary Control Devices (by stack number - use supplemental sheets as necessary).
Stack No.
Manufacturer
Type
Model
CFM
lb / hr
Inlet Gas Temp.
Outlet Dust Rate
F
lb /hr
V olume of Gas Handled
1-1 =t Dust Rate
Collection Efficiency
0/0
Method of Disposal of Collected Materials
Secondary Control Devices (by stack number - use supplemental sheets as necessary).
Stack No.
Manufacturer Type Model
Volume of Gas Handled CFM Inlet Gas Temp. F
-
Inlet Dust Rate .l.b.lhr Outlet Dust Rate lb /hr
Collection Efficiency 0/0
Method of Disposal of Collected Materials
If control devices are wet scrubbers:
gal/min
Pressure
psi
Water Flow Rate
Method of waste water disposal
This is to certify that the above information is true and complete to the best of my
knowledge.
Signature
Title
Date
Return complete form to:
Kansas State Department of Health
Division of Environmental Health
Air Quality and Occupational Health Section
State Office .Building
Topeka, Kansas 66612
84
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