STATEWIDE INVENTORY
OF
AIR POLLUTANT EMISSIONS
STATE OF KANSAS
-------
PEDCo-EN VI RON MENTAL-
SUITE 8 ATKINSON SQUARE
CINCINNATI. OHIO 45346
513 IT7 1-433O
STATEWIDE INVENTORY
OF
AIR POLLUTANT EMISSIONS
STATE OF KANSAS
1970
-------
TABLE OF CONTENTS
Page Number
1.0 TASK DESCRIPTION-. 1
2. 0 AREA DESCRIPTION 2
3 . 0 METHODOLOGY 4
3.1 Point Sources 4
3.2 Area Sources - Fuel Combustion.. 5
3.3 Area Sources - General 16
4. 0 AREA GRIDDING 29
4.1 Sedgwick County 29
4. 2 Shawnee County 31
4.3 Leavenworth and Johnson Counties 32
4.4 Wyandotte County . 32
4 . 5 Area Maps 33
-------
1.0 TASK DESCRIPTION
This report presents the results of the emissions
inventory for the State of Kansas. The purposes of the
study were:
1. To calculate the emissions of air .pollutants
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:
0 Particulates
0 Sulfur Oxides
0 Nitrogen Oxides
0 Carbon Monoxide
0 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.
-------
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.
Maps of the grid systems for Sedgwick and Shawnee
Counties and the Kansas portion of the Kansas City Interstate
AQCR are contained in Section 4.0.
-------
'Northwest Kansas- Intrastate
Air Quality Control Region
(097) . -
North Central Kansas Intra-
state Air Quality Control
Region CO 9 6.)
Northeast Kansas Intra
state Air Quality Control
Region (095)
Metropolitan
Kansas City Inter-
state Air Quality
(094)
CITY
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)
-------
3.0 METHODOLOGY
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,
April 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.
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.
-------
The State Agency tabulated emissions from each point
source by county, with the exceptions of those sources in
Sedgwick, Shawnee, Leavenworth, Johnson, and Wyandotte.
Emissions from point sources in these latter counties are
listed in the computer print out. The computer print out
also lists the county point source emission totals.
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
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 11.3
% Sulfur 4.4
Distillate Oil
% Sulfur .27
Residual Oil
% Sulfur 1.2
Natural Gas
% Sulfur .0001
3.2.1 Residential Fuel
A. Coal
Data; ฐ 1960 Census of Housing - Kansas;
0 Statistical Abstracts of the U.S., 1969;
0 U.S. Bureau of Mines, Distribution of
Pennsylvania Anthracite for Coal Year
April 1, 1967, to March 31, 1968.
0 Air Pollutant Emission Inventory Techniques,
Unpublished Report, E.P.A., GAP, Bierbaum, P.G,
and Gedgaudas, M.J.
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 the appropriate factor from the
Emission Inventory Techniques document. 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%. Residential
coal was apportioned to individual counties by using the
ratio of number of dwelling units which use coal for space
heating in a county to the six Region total for such dwelling
units. 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; ฐ 1960 Census of Housing - Kansas;
0 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
-------
unit. 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 appropriate factor from
the Emission Inventory Techniques document. 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; ฐ U.S. Bureau of Mines: 1969 Minerals Yearbook,
Natural Gas Preprint;
0 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
-------
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; ฐ U.S. Bureau of Mines, Mr. L. WesterStrom,
(703) 557-1350;
0 U.S. Bureau of the Census, Census of
Manufacturers: 1963. Fuels and Electric
Energy Consumed in Manufacturing Industries:
1962.
0 U.S. Department of Commerce, 1967 Census of
Business-Wholesale Trade, Kansas;
0 U.S. Department of Commerce, 1967 Census of
Business-Retail Trade, Kansas;
0 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
-------
was determined by subtracting the following from this amount:
the point source industrial coal 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. The commercial-institutional coal was apportioned to
individual counties using a factor computed as follows:
County Apportioning Factor = [1/3(|) + 1/3(^) + 1/3(|) ]
where:
A = number of retail establishments in a county
B = number of retail establishments in the six Regions
C = number of wholesale establishments in a county
D = number of wholesale establishments in the six Regions
E = county population
F = six Region population.
B. Distillate Oil
Data; ฐ U.S. Bureau of Mines, Sales of Fuel Oil and
Kerosene in 1969;
0 U.S. Department of Commerce, 1967 Census of
Business-Wholesale Trade, Kansas;
0 U.S. Department of Commerce, 1967 Census of
Business-Retail Trade, Kansas;
0 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; ฐ U.S. Bureau of Mines, Sales of Fuel Oil
and Kerosene in 1969;
0 U.S. Department of Commerce, 1967 Census of
Business-Wholesale Trade, Kansas;
0 U.S. Department of Commerce, 1967 Census of
Business-Retail Trade, Kansas;
0 Kansas State Board of Agriculture, Population
of Kansas by Counties - 1970.
Procedure; The quantity of oil listed in the 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
-------
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; ฐ U.S. Bureau of Mines: 1969 Minerals Yearbook,
Natural Gas;
0 U.S. Department of Commerce, 1967 Census of
Business-Wholesale Trade, Kansas;
0 U.S. Department of Commerce, 1967 Census of
Business-Retail Trade, Kansas;
0 Kansas State Board of Agriculture, Population
of Kansas by Counties - 1970;
0 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:
-------
0 Arkansas - Louisiana Gas Company
0 Central Kansas Power Company
0 The Gas Service Company
0 Greeley Gas Company
0 Kansas-Nebraska Natural Gas Company
0 Northern Natural Gas Company
0 The Tri City Gas Company
0 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.
-------
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; ฐ U.S. Bureau of Mines, Mr. L. Westerstrom,
(703) 557-1350;
0 U.S. Bureau of the Census, Census of
Manufacturers: 1963. Fuels and Electric Energy
Consumed in Manufacturing Industries: 1962.
0 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; ฐ U.S. Bureau of Mines, Sales of Fuel Oil and
Kerosene in 1969;
0 U.S. Department of Commerce, 1967 Census of
Manufacturers, Kansas.
-------
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 factors developed for industrial coal apportionment.
C. Residual Oil
Data: ฐ U.S. Bureau of Mines, Sales of Fuel Oil and
Kerosene in 1969;
0 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; ฐ U.S. Bureau of Mines: 1969 Minerals Yearbook,
Natural Gas;
0 U.S. Department of Commerce, 1967 Census of
Manufacturers, Kansas.
-------
Procedure; From the Bureau of Mines Yearbook, natural
gas usage figures were obtained for the following industrial
categories:
0 "industrial use"
0 "lease and plant fuel"
0 "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 account for this quantity of gas.
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: ฐ 1968 National Survey of Community Solid Waste
Management Practices, EPA. Cincinnati, Ohio;
0 Acreage of Rangeland Intentionally Burned,
Cooperative Extension Service, R.M. Hyde,
Kansas State University.
-------
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.
-------
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 burn-
ing 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.
All emissions from solid waste disposal operations were
listed as area sources with the exceptions of the open burn-
ing dumps in the Kansas portion of the Kansas City Interstate
AQCR. However, many of the dumps in this AQCR have ceased
burning in either 1970 or 1971. The conical burners in
Dodge City (Ford County) and Garden City (Finney County)
were listed in the Section V tabulation as "On Site - Area
Sources". Other emissions included in this category 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" include those from open burning dumps
where the burning may be either "planned and limited" or
"unlimited" plus open burning of uncollected refuse. Emissions
-------
TABLE 3.1 KANSAS ARGICULTURAL BURNING BY COUNTY
AQCR
REGION
095
096
098
099
COUNTY
Marshall
Osage
Pottawatomie
Wabaunsee
Geary
Morris
Riley
Chautauqua
Cof f ey
Elk
Greenwood
Lyon
Wilson
Wood son
Butler
Chase
Cowley
ACREAGE 1
BURNED
10,
5,
30,
50,
20,
40,
25,
10,
5,
20,
70,
40,
5,
5,
20,
60,
5,
000
000
000
000
000
000
000
000
000
000
000
000
000
000
000
000
000
TONNAGE
BURNED
3
1
10
17
7
14
8
3
1
7
24
14
1
1
21
1
,500
,750
,500
,500
,000
,000
,750
,500
,750
,000
,500
,000
,750
,750
700
,000
,750
PART.
30
15
90
150
60
120
75
30
15
60
210
120
15
15
60
180
15
EMISSIONS (TONS/YEAR)
S02 CO HC
175
88
525
880
350
700
440
175
88
350
1225
700
88
88
350
1050
88
35
18
105
180
70
140
90
35
18
70
245
140
18
18
70
210
18
NO
X
3.
1.
10.
18
7
14
9
3.
1.
7
24.
14
1.
1.
7
21
1.
5
8
5
5
8
5
8
8
8
-------
from rangeland burning are listed in the separate category
of "Agricultural Burning".
3.3.2 Motor Vehicles
Data; ฐ 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;
0 Topeka and Wichita Functional Classification
Maps: Traffic Count Data, State Highway
Commission of Kansas.
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.
For Shawnee and Sedgwick Counties, traffic maps were
used to estimate vehicular emissions in each grid using the
traffic count method.
-------
The motor vehicle emission estimates made in the
previous OAP survey were used for the Kansas portion of the
Kansas City Interstate AQCR.
3.3.3 Motor Vehicles - Diesel
Data; ฐ Revenue from Sale of Diesel Fuel in Kansas,
Department of Revenue, Motor Fuel Tax Division,
Walter Dunn, Chief (913) 296-2411;
0 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: ฐ 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
questionnaire requesting 1970 data on the number
of flight operations 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
aircraft, the following assumptions were made :
-------
Type of Operation
Air Carrier
Military - Itinerant
Civil - Itinerant
Civil - Local
Military - Local
Type of Aircraft
95% is jet powered.
Three engine.
80% jet, 20% piston.
65% two engine, 35% single
engine.
80% piston, 20% jet.
65% single engine, 35%
multi-engine.
90% piston, 10% jet.
70% single engine, 30%
multi-engine.
90% jet, 10% piston.
90% multi-engine, 10%
single engine.
Emissions from operations at the Fairfax Airport,
Wyandotte County, were estimated by the Wyandotte County
Department of Health.
3.3.5 Vessels
Data; ฐWaterborne Commerce of the United States;
Department of the Army Corps of Engineers,
Part 2 (p. 13, 1969).
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
-------
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: ฐ U.S. Bureau of Mines, Sales of Fuel
Oil and Kerosene, 1969;
0 U.S. Department of Commerce, City and
County Data Book, 1962.
Procedure; The total quantity of fuel oil used by
railroads 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 was subtracted from
this total; this quantity was 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.
The quantity of fuel oil used in the six Regions 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.
-------
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.
Railroad emissions estimates developed in the previous
GAP survey of the Kansas City AQCR were used for that region.
3.3.7 Gasoline Handling and Evaporation
A. Fuel Storage Evaporation Losses
Data; ฐ Petroleum Facts and Figures, 1967 Edition,
page 160.
0 Compilation of Air Pollution Emission
Factors, Preliminary document, April 1971.
Procedure; Kansas has a total fuel storage capacity of
125,434,000 and 27,492,000 gallons of gasoline and kerosene
respectively. To calculate evaporation emissions, the total
kerosene capacity was multiplied by 135/238 to compensate.for
its lower volatility. The corrected kerosene plus gasoline
storage capacity of 140,829,000 gallons x^as used to calculate
emissions.
Breathing losses from fixed roof storage tanks were
calculated using appropriate emission factors and assuming
-------
that 75% of the total fuel storage capacity is of the
fixed roof variety.
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: ฐ 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;
0 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 hydrocarbons per
thousand gallons of gasoline.
3.3.8 Solvent
A. Dry Cleaning
Data; ฐ 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.
B. Paint Solvents
Data; ฐ 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:
n 4 o\ / p -; -i n\ # of manufacturing employees (county)
(2515 8) X (1) X * of Itianufacturin9' 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:
0 A price range of $4 to $7 per gallon.
0 10% to 60% solvent content.
0 The fraction of the total sales for the particular
type of paint or allied product considered.
Paint solvent emissions were calculated using the
following formula:
(1 x IQk) X ^ Millions Dollars (county) = Tons/Yr. Paint
Solvent Emissions.
C. Ink Solvent Emissions
Data; ฐ 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
$367 million. Ink usage was apportioned to the counties
according to the following formula:
-------
(14.2) nfi7^ y # of manufacturing employees (county)
(2515.8) ^b/J A # of manufacturing employees (state)
= $ million ink (county).
Ink solvent emission estimates were based on the
assumptions that ink costs $0.30 per pound and has a
60% volatile content. The following formula was used:
TnV
Solvent (Tons/Yr ) - ($ Million Ink Sales, County) (.6)
(TฐnS/Yr') ~ (ง0.30/lb.) (2,000 Ib/ton)
-------
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 comercial acreage,
-------
since the 1960 actual land use data were incomplete. The
apportioning factor for each grid was the ratio of commercial
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 county
total of such acreage.
Motor vehicular emissions in a grid 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 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).
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.
-------
4.3 Leavenworth and Johnson Counties
The ratio of the population in each grid to the county
population was used to apportion the following:
0 domestic fuel usage
0 commercial-institutional fuel usage
0 open burning
0 incineration
0 solvent evaporation.
Industrial fuel usage was apportioned by inspection of
area maps. Motor vehicle emissions, both gasoline and diesel,
were previously calculated in the OAP survey. 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
Emissions in Wyandotte County were previously estimated
and apportioned to grids by the Wyandotte County Department
of Health. The emissions were presented as a grid total. ,
Included in the totals, where applicable, are the emissions
from the following sources:
0 residential fuel combustion
0 commercial-institutional fuel combustion
0 industrial fuel combustion
0 mobile sources
* motor vehicles * aircraft
* railroad * vessels
0 solid waste disposal.
-------
Solvent emissions are listed separately under
hand calculated emissions.
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
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.
-------
4190
4180
4170
4160
i4150
605
615
625
FIGURE 4.1 - UTM GRID SYSTEM FOR SEDGEWICK COUNTY
-------
CO
Cn
4345
4335
4325
4315
4305
265
275
255
FIGURE 4.2 - U-TM GRID SYSTEM FOR SHAWNEE COUNTY
-------
4380
370.
360
.350
.4340
4330
4320
310
300
7-M/ CO.
JAC.XSfl.-V Ofr.
4290
320 330 340 350
-36
Figure 4.3 UTM Grid System'-for the Kansas Portion of the.
... . Kansas City Interstate AQCR..
-------
... f
Figure 4.4 Location of
Point Sources Emitting
Over 100 Tons Per Year
in Segwick County
8 : GXELCY TV/?.
EAGlc TV/?.
f
f
A
j .1
if
SHE.7MAN TV/?.
G.7ANO RfVEff TV/?.
EN ?:A;,V TVV?.
MORTON TV/?.
TON* TW?.
EWE TW?.
i ..
V/OLA TV/?.
54
51
l5y C=N7E3 TV/?.
rA"?c TV/?.
JSANT TV/?.
~'i,.,J:<.~CK/ TV/?
X'lwn-ryzr..? jrJs'.*rr.*.'.; *
ATTfCA TV/?.
h
fJBClS ^:1Sฃ:I* 'f-53^--
_;. . _.__ .'"':"".-_. '"" > .'".
/LL.'.VC/S TV/?.
T
(4 _ss?<;v/'ex '
5 ..'. i5.V..:.:.,'S.W-.
*' i;i.,;-'K,
I ;"^T^?'|^;31,;34 ป|;^t**ป
H4190
J5~ ~ "tj ~
$ //.'N'NEr A I1//?.
605
SALE// TV/?. . < .^OCMTC"^ T//?.
/
44180
f4170
615
625
635.
-------
U)
00
.-ft.
I i
~>:.v i
:: ' "ปJ.
! !
- CI I .
J"li ' It^
i i
i
ป>
- i
$ i
l
9 !
1
1 *'
1
/W. LAK
-H
f -
ซ H
B '
^ ;
Jfc'-* r
4
*^
1 i
J [ I
I (
|
i i
1
: ! i
Kino!.
i .'"
|
1
1
. 1
i i
i :
j ;
i j
i r
i i
: ! /
; .
~^^^^-^a=.
s N c K ;: N
v r r ?.
I? !
11 i -
IB i
: T i
i ELMONt
'
::
|'-3 -3
V f
Si / 7
1* - iu ' ' -' "n
\^-!k:-Li^l.Sju^aJ
^t
H ! I DOVER
H ' I '
; "-.r*--^-^^"
. '.,"."1 i
SCALE IK MILES
>] U | til : ... // "i i S
^ iT J 1 ; : ff \ ." BSPnyTON ^J[J_
N I T f i}if;^ ,vr . I- ,- ' ' - v "?-' 41
t|| L I, ,j I |! ,_ i ! jf ; ij ! H "V"^ T 4?
ILL
Ik
.0 O
I ฐ
"jWA^AKUSA^r
I . \v.
HIGHLAND
4345
4335
4325
4315
^=^
245
255
265
^ 4305
285
Figure 4.5 Location of Point Sources Emitting Over 100 Tons Per Year
-------
Sv.4-eP>
*.
Figure 4.6 .Location of Point Sources Emitting Over 100. Tons
Per Year in the--Kansas" Portion of the Kansas City
. . . Interstate AQCR. " . ' .
-------
Table 4.4 POINT SOURCES IN SEDGWICK EMITTING 100 TONS
PER YEAR OF MORE OF ANY POLLUTANT
Source # Firm
3 - Wichita Flour Mills
5 Furley Grain
8 Ross Industries
20 Vulcan Chemical Co.
23 McConnell Air Force Base
31 Grede Foundries
32 Service Iron Foundry
33 Ferrolay Foundry
36 Ehrsam Wichita Foundry
42 Standard Press Steel
45 Cargill Inc.
50 Kansas Gas & Electric
51 Kansas Gas & Electric
53 Kansas Gas & Electric
54 Garvey Grain
56 SP Wallingford
57 Ross Industries
58 Wichita Flour Mills
64 Ritchie Construction
74 Derby Refining
77 Derby Refining
-------
Table 4.5 POINT SOURCES IN SHAWNEE COUNTY EMITTING 100
TONS OR MORE OF ANY POLLUTANT
Source # Firm
6 Ismert-Hincke
7 Thompson-Dehydrating
21 Berry Grain
23 Ismert-Hincke
25 Topeka Terminal Elevator
27 Rodney Milling
33 Goodyear Tire and Rubber
35 Concrete Material
37 Kansas Power & Light
38 Kansas Power & Light
-------
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 print-outs, and the country point source emission
totals and fuel usage listings prepared by the Kansas
State Agency.
Figures 5.1 through 5.7 provide a visual summary for
each AQCR of the major sources of emission of each pollutant,
-------
Table 5.1
EMISSIONS INVENTORY SUMMARY
For the State of Kansas
Kansas Portion of the Kansas City Interstate Air Quality Control Region
Data Representative of Calendar Year 1970
SOURCE CATEGORY
;. FUEL COMBUSTION
A. Residential Fuel-Area Source
1 . Coal '
. Distillate uii 1
3. Natural Gas
4 . Wood
. otner
. 1U1AL n
B. Comm.-Instl. & Industrial
l.a Bituminous Coal-Area Source
Tons of Pollutant/Year
Part.
5V
33
S02
CO
/ / o / %ฃ"
81 //
HC
// <^/
7
N0x
/9
7 93~ F9&
\
33A 'H5 ^33 ฃVS-
-Wir^ lA'JV-/
c^J'-x'c?^"' \MMCt
1
937
^/9
1
$"?.J99 \7~cN3
i
^269 S^v-S'lXSW
/ฃ> i <7ฃ ; 3 <ฃ,->
I/ o i /r v
Co os ' v ) /
(*?
A/ ฃ 4/ ! A'6> /
/^.j1 i S '
1
1. Anthracite Coal i \
2. Bituminous Coal
J nic:1-illat-r> Oil
5. Natural Gas
D. TOTAL FUEL COMBUSTION
ix. PROCESS LOSSES
\. Point Sources
5. Area Sources ~ ~~
III. SOLID WASTE DISPOSAL
i. Incineration
l.a On Site Area Source
l.b On Site Point Source
S^o /^/^^ / 3 3 > 3*/7 \&769>
j
i |
jfS1 V 3 i ^'/^ /9-vS7
/ฃ?? !<ฃ/5V i a?V ( /c? l^?6''tf>5"
^9c^ U^^CJi /_^'<0 6ฃfo l/^ ^tef
ฃ8
!
J
i
t
i
i
i
/5oC \ &
-------
EMISSIONS INVENTORY SUMMARY
Page 2
SOURCE CATEGORY
Tons of Pollutant/Year
Fuel,etc.
III. SOLID WASTE DISPOSAL (Cont'd.)
B. Open Burning
C. TOTAL SOLID WASTE DISPOSAL
IV. TRANSPORTATION- AREA SOURCE
VCSSEJ-S ' ~ __-__- ซ. __._,
H. TOTAL TRANSPORTATION
V. MISCELLANEOUS-AREA SOURCE
oOJLVGnu -- --* '- -. ..-.-_,_--.
C. TOTAL MISCELLANEOUS
VI. GRAND TOTAL
AAPva cnm?riTr _ ______ _ _ __ _
BTDOTMT" Cf"m'Dr1'P ______ _ _
. IrUXlNl oUUK^ij ______ -.__ _ _ _
Part.
vo/
so2
^5-
CO j HC
,2/30
7/^ /^ M9&
/%ฃ&
&3ฃ
/*/ I4ฃ?<6^
^76 l/9/:d6/
$96 \/(=,o/
/3H
7
ฃ%$0
346S
N0x
?S& /SO
//?'&/&
A/A37A
}
el&ZS
/V
3oVf
ye>. 393
ฃ 7^9
ฃ^q
399.&&\3?.*/7/\
SO. WO
f TTITAT.- _ 1 2^i ,/i&
W?o
6 05^6
~ฃ ^ C'} --"/X ! , . rt / *ns
%&6d\/3,ซ?ฃ\
^"/^ A C />
.
-------
Table 5.2
EMISSIONS INVENTORY SUMMARY
For the State of Kansas
Northeast Intrastate Air Quality Control Region
Data Representative of Calendar Year 1970
SOURCE CATEGORY
I. FUEL COMBUSTION
A. Residential Fuel-Area Source
. coal
2. Distillate Oil 1
3 . Natural Gas
. wood . . i
. otner
. TOTAL - 1
B. Comm.-Instl. & Industrial
l.a Bituminous Coal-Area Source
b Bituminous Coal-Pt. Source
3. a Distillate Oil-Area Source
5. a Natural Gas-Area Source
C. Steam-Electric Power Plant
2 . Bituminous Coal
3n i" cr -1- -i 1 1 n -t- o Oil _
Tons
Part.
I5&
41
344
440
1
27
B
ss-
1 r"j
30&
_jOvT
96 /
of Pollutant/Year
S02
Il4(y
181
3
CO
,?42
M
ISO
1330 ]ฃ-/(,
i
HC
81
n
NO
X
J??
53"
ฃ/ ^-77
Fuel, etc.
Quantity
/3 700
Unit
7~Sns
- ! 64
10 \ - 2L Itofi
ฃ / ! 2_
45-3
4>
7 1 94 !5"6O
1
J^3^
!
^/- /Q i /x/2 /
-<? i 1248 \ k 'Gซt
MS
47
2^0
2 .? 202: 905
i i
! i
M43 1 204 ^794 5804
274
^
6. Other
D. TOTAL FUEL COMBUSTION
11. PROCESS LOSSES
A. Point Sources
3. Area Sources
III. SOLID WASTE DISPOSAL
\. Incineration
l.a On Site Area Source
l.b On Site Point Source
II a i
2^4
J4 98k
Sit
1
i
3770 O / ฃv /X"/** /
^/f** t ; /\ Of< I
/7 ?^c/
i
S/5"C>
^579 ! 9,B7L/^57 JZ6/5
O
/e
r!
240 i /96
i 2 2. 7 /
/// ^75 7 22^: ?2/ ! 1 41.^OO\ f^<.
t ' ; *
t i
-------
EMISSIONS INVENTORY SUMMARY
Page 2
SOURCE CATEGORY
Tons of Pollutant/Year
Fuel,etc.
III. SOLID WASTE DISPOSAL (Cont'd.)
B. Open Burning
a un oi ue /ireo. source
2. a Dumps Area Source
2ซb Dumps Point Source"
C. TOTAL SOLID WASTE DISPOSAL
IV. TRANSPORTATION- AREA SOURCE
Motor Vehicles Diesel ~~ ฐ~ ~*
. uii uignwciy rue-L usage
C7\ "i V* <"IT* \ f !
. 1\ ci 1 JL IT U dU. ~ -
E. Ves sels"-""
F. Gasoline Handling ~ ~
Gf\l- V\^^-v* .. ...ซ_ซ_ _ป
. uT-iiei t __ ______
H. TOTAL TRANSPORTATION
V. MISCELLANEOUS-AREA SOURCE
O \J X V (JI1 U
C. TOTAL MISCELLANEOUS
VI. GRAND TOTAL
AAPwa conpr1!? _ ____ _ _ ___
. j!AJ.\Ji/-V oUUKl^Jlj ____ ___
BDrvTMT" CPim3r<17___ _ __ _ _
. JrvJJ.lNl oUUKL-Ji
Part.
/?yฃ
so2
CO :
/Jf \/0,303
c37ฃ
aes'
Jxs~
ฃ3&
t/-30
330
n?
5W
HC
I
J&ZV
/I, WO
N0x
9ฃt*
3~9<3 -^
94?
Quantity
J#j. V3V
Unit
7^/vCs
/ff3.33&,A?.3S-/ \ฃ4&?3\J.09*,9<3/ KY
&W& V?3-
?/ฃ>3
ฃ9/
/V2V\/ฃ3,5$$
' /& 6, S-
.
/^#
/9o?
f*/
/3(*S(
3B.3A&
338
/ฃ,/ฃ
/-, oฃT3
<33/
^$3
32 /os
34
jy
/ฃ, g?y
\S<^ \ra>/$
i
SJ'S? . f/22 \/?^ฃ'A\^. ฃ43 \.U ^v\
/C,.36(> /^^ ฃg%
no on
ir\s\ *\ s /
/25Z
j S JJ? ItS)^*
9^?
^//"5 ฃ3s">
i
-------
Table 5.3
. EMISSIONS INVENTORY SUMMARY
For the State of Kansas
North Central Intrastate Air Quality Control Retion
Data Representative of Calendar Year 1970
SOURCE CATEGORY
;. FUEL COMBUSTION
A. Residential Fuel-Area Source
1. Coal
. Distillate un n
. Natural bas
4 . Wood '
Tons of Pollutant/Year
Part. SO2 CO
79 ฃ8 ? /7*/
HC
4&
ฃ9 104- / 3 8
//7 y /A3 -5O
N0x
/ ^>
JA
Fuel, etc.
Quantity
4 9 ?o
Unit
7o/^c3
j"^69 IA'^/?/
y<ฃ ^ i /^ 5 /^" i/v/yc/1
5. Other i
B. Comm.-Instl. & Industrial
l.a Bituminous Coal-Area Source
b Bituminous Coal-Pt. Source
3. a Distillate Oil-Area Source-
iNcilZU-L a. J_ v-iclS r L, . oOU-uCe '"" "" '
<2&3 67* 3/0 \ /ao
,5V/
c^?56 4"? .
3 ' S^
/ 9 ' 1 55 !
^9 ^t
B i 6ฃ~\ ! 6
/96> i & ?& : 308"
V*? x%*ฃ4 \/<&fiL
ฃ./ &, 9 / ix4/?/
/*S9ฃ> \e3/c2&ฃ HMC-f-
SO <ฃ / i /ฃ5~ &$?9 ?&>&*/ \MM(L}
4*7 ' ฃ / ' /oฃ~ ^-S'^/ ^ฃฃ~O 1/y/VcZ./
:
b Other-Pt. Source j i 1 i
8 . TOTAL '
C. Steam-Electric Power Plant
|x~~ sj *o ' ** ^ ^ / c-*^y * / /*i / t *i c-1 *o c? t
ป-j _/ c?v : - J - - / o v t> ^ fc? ' ^<_o '^ 7 '
1
i
! i
2. Bituminous Coal j . \
3. Distillate Oil i j
4. Residual Oil (
6^ -f" V\ <-!kV* _i i
7 TOT1 AT ~ ซ
D. TOTAL FUEL COMBUSTION
ii. PROCESS LOSSES
\.. Point Sources
5. Area Sources
III. SOLID WASTE DISPOSAL
^ Incineration
l.a On Site Area Source
.D Un bite irOinu bource
\
\
\
\
ฃ i /^ /^? ^5~ y^S"*? '*- /^^B !/<ฃ?,ซ'
^?/ < 1
i 4^>~ ^"^9 3<9SA MMC.t
<57 i /7 ! /4^ S'd 7/^ !
^o&Z
/#7<5/ 1 &<-/ฃL.4\ && \ /ฃ&>o yg3
t$O64
t
\
-------
Page 2
EMISSIONS INVENTORY SUMMARY
SOURCE CATEGORY
_
III. SOLID WASTE DISPOSAL (Cont'd.)
B. Open Burning
ci un o i cs /iirea. oouiu-e
. D un oite irOint oource
a. L/UlUpS /\3_ Go. oOUJTCS
C. TOTAL SOLID WASTE DISPOSAL
IV. TRANSPORTATION- AREA SOURCE
MotO3T VGniCJ-GS DlGS GJ_
VGSSG.LS ~ .
GrH-K/--n~
\j unsir
H. TOTAL TRANSPORTATION
V. MISCELLANEOUS-AREA SOURCE
/vyji -LuuJL L.UJI ctj. jDUJ- iiiny T
OOJ-VcIlL. .
C. TOTAL MISCELLANEOUS
VI. GRAND TOTAL
. /\KJjA oUUKv^Ili ~ __
. .rUJLJNJ. oUUKCri
r* nnrinnaT
Tons of Pollutant/Year
Part.
/13ฃ
so2
/Qi
1
/?aa
^ฃ6
/O^
3/6"
/ V8- 3/9
ฃ?
//0ฃ
ฃS6-
ฃฃ6~
90
Altf
/ooo
CO , HC
10V/
NO
X
Fuel ,etc.
Quantity
3/9 / &38\ฃ./<ฃ,'?<:L//
\
964/
///.ฃTO/
ฃ/ฃ& \i 1,93 5"\ /, &9ฃ$
/V9o
J&f
ฃ/3
/40ฃ
ฃ4,663
360
\ 11 1
/Wo
/o/ /
//9\
2A6
&Wf>8
& S3 9
*36\ ฃ9,?$-0
3o
'
3146, \2S9S \/aX.4ฃ/\Zo,7e}9\A366ft
/P/P34
A
-------
Table 5.4
EMISSIONS INVENTORY SUMMARY
For the State of Kansas
Northwest Intrastate Air Quality Control Region
Data Representative of Calendar Year 1970
SOURCE CATEGORY
[. FUEL COMBUSTION
A. Residential Fuel-Area Source
1. Coal
Tons of Pollutant/Year
Part.
2. Distillate Oil 1 /7
3. Natural Gas i 7?
SO2
3$^
6?
A
CO
/oo
% /
4 . Wood '
5. Other ~~
HC
ฃ y
j-
3A
6. TOTAL i /Iฎ i -^i? /<3o &,/
B. Comrn.-Instl. & Industrial
l.a Bituminous Coal-Area Source
b Bituminous Coal-Pt. Source
3. a Distillate Oil-Area Source
lNdi,UX. ctj. kjclS -trU. oOUITCe "- .
t> . PJCOCGSS GclS Pt. SOUjfCG
8T1 C\ T1 A T
C. Steam-Electric Power Plant
5M a -I- TI Y- a 1 f"1 a c! ___._ ซ .- _ _ _
6f\ 4- l-\ ,**. Y*
7m /-vm AT _ .
D. TOTAL FUEL COMBUSTION
11. PROCESS LOSSES
'\. Point Sources
J. Area Sources '
III. SOLID WASTE DISPOSAL
v. Incineration
l.a On Site-Area Source
l.b On Site-Point Source
/ฃl
/ O 3 V & K Gtjl
//*/O /&,63^ \frA?(2f
^/9^ ฃ&,*// \fif-icf-
^ 1 ^3 ^ i /ฃ? ^-S"
ป
; .i
390 3ifd? /^'S1 ซ .^f? /ffAs"*
1
) !
i
j i
i
I
6~/6 \MMCl
\
\
i
\
, gฃ | /4/^,~ c^^^)"" ^".5" ^"
_^7 ' ^_ i5 /% \/8ฃ&
\
/9 \J.o6o \ 6/3 f3A W/
i
-------
Page 2
EMISSIONS INVENTORY SUMMARY
SOURCE CATEGORY
Tons of Pollutant/Year
Fuel,etc.
Part.
III. SOLID WASTE DISPOSAL (Cont'd.)
B. Open Burning
/aa/
so2
S3
CO HC
90 / &\ ฃ VI '6
N0x
Quantity
49&V&&; o#9
Units
7b/V5
V.
. TOTAL SOLID WASTE DISPOSAL
TRANSPORTATION- AREA SOURCE
Motoir VGniclss Di. oo.-Lvenc ~ ___
. TOTAL MISCELLANEOUS
. GRAND TOTAL
AT?WB cnnDr"!? ____ ____ _______ __
!T3(^lTMT< Cnt1T?r'T?~_ _ _ ____ __
. JrUXINi oUUKCJCj
1 TnTftT.- _
/&ฃ!
^/S"
ฃฃฃ>
69
7/0
S3
-?o/&
dP5V|?6,?/d
33.1*
120
7S9
ayii>
ซ9f
/6,A~/& \/V.396\/,^S&,.?36\/{fc///s
ฃ3VS\ yt>%\a&3ฃ\ /W3V\KYf#f4.-
/9^
%f$&
476 !
&V90 \J,^^ V&,^'3\ฃA,
-------
Table 5.5
EMISSIONS INVENTORY SUMMARY
For the State of Kansas
Southeast Intrastate Air Quality Control Region
Data Representative of Calendar Year 1970
SOURCE CATEGORY
;. FUEL COMBUSTION
A. Residential Fuel-Area Source
1 Coal-:
Tons of Pollutant/Year
Part.
1\U
2. Distillate Oil i /ฃ"
3 Natural Gas ' /ฃฃ~
4 . Wood j
S02
/} /Jr /) ^**
-5 'b
y
5 Other 1
6 TOTAL i a.*?*/ ?.*,Qr7
B. Comm.-Instl. & Industrial
l.a Bituminous Coal-Area Source
b Bituminous Coal-Pt. Source
3. a Distillate Oil-Area Source
1\ a UUJTci JL vj<3.o JL I- oOUZTCG
S^m1 AT .--,.-__-_ _ _ __
C. Steam-Electric Power Plant
* ^^,5 ! ^^5
1 v
CO
6,9 6~~
HC
S ฃ Sj
f fj f
7 ! ฅ
5 ' B
X 3'4 ! ฃ&*S
9O A3
ฃฃฃ./ ฃฃ>
i i
! ฃ> /
5~ฃ>
N0x
9o
/ i?
Fuel, etc.
Quantity
Of?, ฃO &>
Unit
7"7R \ ฃ&>/0 >&&>-L
i /96 i 6 6<5 ! .3ฃeU/3~<39 i ///9O l/^/v-v
i 79 i c5 /
< i
/? 9
JtfQ ! PH' 9 / i/y/r'^:/
t
i
i ; i i
^ / <3 /
i <ฃ> 7 /
j F ^ t> ' ^25 7Q
\ \
/ \ /&4\ ^6^ \ฃ?.o/A \X6fiL
f?4 \ 699
3/ao \ i
i
1.
2.
3.
4.
5.
6.
7.
Anthracite Coal
Bituminous Coal
Distillate Oil
Residual Oilf-
-)
i _ ; ,/ i
J- IT'
1 !
^ -._ _ .. j J
/^( i 5^ ! A
\ !
, . / r-
cซ / o * : ^2 v j o I 7* c5 /V-*^
.
! 1
J? 7
Other-
TOTAL-
.3
ป eg// id
'I
.3 A
D. TOTAL FUEL COMBUSTION
II. PROCESS LOSSES
i. Point Sources-
'. Area Sources
III,
SOLID WASTE DISPOSAL
i. Incineration
l.a On Site-Area Source--
l.b On Site-Point Source-
ฃฃ.
M&22-
-------
Page 2
EMISSIONS INVENTORY SUMMARY
SOURCE CATEGORY
Tons of Pollutant/Year
Fuel,etc.
Part.
so
CO
HC
Quantity
Unit:
III. SOLID WASTE DISPOSAL (Cont'd.)
B. Open Burning
l.a On Site-Area Source
l.b On Site-Point Source
2.a Dumps-Area Source
2.b Dumps-Point Source [
C. TOTAL SOLID WASTE DISPOSAL
IV. TRANSPORTATION- AREA SOURCE
A. Motor Vehicles-Gasoline
Motor Vehicles-Diesel -
B. Off Highway Fuel Usage
Cป Al_TGX"cljLt"" "" ""* *"* ซ
D. Railroad
F. Gasoline Handling
G("\4-'K/-iV__ ,__ ,_____._._-. _______._.__
VJUIlt^J- , . . .- .-*
H. TOTAL TRANSPORTATION
V. MISCELLANEOUS-AREA SOURCE
A. Agricultural Burning
C. TOTAL MISCELLANEOUS
VI. GRAND TOTAL
A. AREA SOURCE \ H/>3 \-l6oJ-
\
SV&V/ 51 o 2 \fW.md.
/99,79V
30 9
,*?/
-------
Table 5.6
EMISSIONS INVENTORY SUMMARY
For the State of Kansas
South Central Intrastate Air Quality Control Region.
Data.Representative of Calendar Year 1970
SOURCE CATEGORY
I. FUEL COMBUSTION
A. Residential Fuel-Area Source
2. Distillate Oil 1
Tons of Pollutant/Year
Part.
*TO
90
3. Natural Gas 1 12.4
4 . Wood 1
5 Other 1
S02
7 /V Ci
76
rf
CO HC
// o ฃ&
/O 6
NO
II
r?9(22
4P9 / 3 tfStf
Unit
/ r>n<*
K&cJ
Mftirf
6 TOTAL j Iฐl4 i 4/7 ฃ*4 S2?>
B. Comm.-Instl. & Industrial
l.a Bituminous Coal-Area Source :
b Bituminous Coal-Pt. Source
3. a Distillate Oil-Area Source
IJIS U-L.L J_d L.G U1J. JrC. oOU-L CG
i\C2b J.UUcUL U1J. Jr U oOUr Ce~"~
ป cl JNo. ULU. dX vjdS AiGd oOU-L CG |
iNdUU-u d.L vjUo L U oOUZTCG 1
Q _
C. Steam-Electric Power Plant
* iNdt-UJL d J. OdS .
7rp|'^nr1 A T ... ซ_...... _...... - . . r-r,,,. -, .-_.... rn
. iuiaj_i - - -]
D. TOTAL FUEL COMBUSTION
ix. PROCESS LOSSES
A. Point Sources
!. Area Sources -
III. SOLID WASTE DISPOSAL
i. Incineration
l.a On Site-- Area Source - -
l.b On Site-Point Source -
1 1 I L
< i i
1321 /97O ^4/ ฃ2.
2 I3&\ 12. 4
i
& / / 5-8 / ! / 2
^3 9ฃ>
1 /^-*
! 7
/Si" /5-W! 2 2^
" 27 /^ - i 2
/32 d^5 S~ฃ4 /tin}
1 2A20 b^^c
} i
24 5 i P//2 I K(~*/
/ /o o sA^ i Q. / 7 6 l/W/w^/
! i
i i
3241 i 40fe7. 5"/fi 5276 AT422
j
j
' i
i I i
^ ^ ' /- /^> ; /"
^ .< h C/ I O>
/O OCii O^7 I <> O
/ cj ^~i / 1 i; i ฃ* ฃ-\
90 1 S~\ 14332,
4O>4 \ 4686 890 ! 48&S~* 3Q27J
/4 98C
7
1
/028I //09 66 / 9032
/,44s"1 3/O
i 46/ฃ
2O6x?" 6/9
6 /9 4/2,996
'i
~TO^(
-------
Page 2
EMISSIONS INVENTORY SUMMARY
SOURCE CATEGORY
I
Tons of Pollutant/Year
Fuel,etc.
Part.
so
CO
HC
NO iQuantity
x
Unit
III. SOLID WASTE DISPOSAL (Cont'd.)
B. Open Burning
l.a On Site-Area Source [
l.b On Site-Point Source !
2.a Dumps-Area Source
2.b Dumps-Point Source
C. TOTAL SOLID WASTE DISPOSAL
IV. TRANSPORTATION- AREA SOURCE
A. Motor Vehicles-Gasoline
Motor Vehicles-Diesel
B. Off Highway Fuel Usage
D. Railroad
E. Vessels
F. Gasoline Handling
H. TOTAL TRANSPORTATION
V. MISCELLANEOUS-AREA SOURCE
A. Agricultural Burning
B. Solvent
C. TOTAL MISCELLANEOUS
VI. GRAND TOTAL
A A "D"H* A Of*\TTT5/~*Tt* ^ i
il-lvl.-JAl. ij\J \J JL\\^J-4 I
f
H T51\ T 'NT rn 011T T "O r* T?
ij ซ Xr Vv Jป i\ JL O v./ U ix Vป^ Jj i
Crnf^rn TV T ^ . / ^ซ / ^j
. JLUl/Ajj lo**?, -> f 7
. 3.
LBIOA
36 go
l.oao |/y
I/C
1^84
^7,04^^
96/\
jf/;AA
-------
Table 5.7
EMISSIONS INVENTORY SUMMARY
For the State of Kansas
Southwest.Intrastate Air Quality Control Region
Data Representative of Calendar Year 1970
SOURCE CATEGORY
Part.
Tons of Pollutant/Year
S0
CO
HC
Fuel, etc.
Quantity Unit
i. FUEL COMBUSTION
A. Residential Fuel-Area Source
1. Coal
2. Distillate Oil i <$S "79 , /JL
3. Natural Gas , 7^ I a.
4. Wood- ! I
5. Other j j I
6 . TOTAL j /A3 \ 277 '
B. Comm.-Instl. & Industrial
l.a Bituminous Coal-Area Source i /?/ !
b Bituminous Coal-Pt. Source 1 [
ซ t-> o jce~~ -"-""~~-""~ ""*"--*" -i j
3.a Distillate Oil-Area Source j /ff I
b Distillate Oil-Pt. Source ; ฃ \
4. a Residual Oil-Area Source 1 /j% !
b Residual Oil-Pt. Source \> \ \
5.a Natural Gas-Area Source i /<=>J? ! i i
b Natural Gas-Pt. Source 1 7^ j / |
6. Process Gas--Pt. Source j 33 j_ [
7. a Other-Area Source ) | [
b Other-Pt. Source j 9^? s I ฃ I
J.
i
C. Steam-Electric Power Plant [
1. Anthracite Coal 1
2. Bituminous Coal ; i i
3. Distillate Oil i
4. Residual Oilf : //
5. Natural Gas j //i?
7 . TOTAL ; /g?ซ?
D. TOTAL FUEL COMBUSTION ' 23B Q^'O j
IJL'. PROCESS LOSSES
A. Point Sources
t. Area Sources
III. SOLID WASTE DISPOSAL
u Incineration
l.a On Site-Area Source F 8 \ _<ฃ \ //
l.b On Site-Point Source ' 1 ! <
779? \MfltCf-
4 '$77
7/
ST
\/<6
-------
EMISSIONS INVENTORY SUMMARY
Page 2
SOURCE CATEGORY
Tons of Pollutant/Year
Fuel,etc.
III. SOLID WASTE DISPOSAL (Cont'd.)
B. Open Burning
. D un oiue iroint oource
.a uumps ^iiSa source
2.b Dumps Point Source ~ ~
C. TOTAL SOLID WASTE DISPOSAL
IV. TRANSPORTATION- AREA SOURCE
A * MotoJT Vehicles Gasoline
Motojr Vehicles~~Diesel ~~ ~*
l\o, 14- X. Odd ~~ ,-.-.,-..--.
VtioocJ-Lo
Gr\4- Vv /->
* u unG.u " -.___. . _
H. TOTAL TRANSPORTATION
V. MISCELLANEOUS-AREA SOURCE
/\cjjC icu j. UUJL o.x liujrniny -. ซ
o o J_ v enc ^-
C. TOTAL MISCELLANEOUS
VI. GRAND TOTAL
. AKJiA oUUKv^Ji __ ___ _ __
r* rpr>T>aT
Part.
7007
so,
ฃ
&3
/C/5"
S<3ฃ
/7t>
$>A
980
ฃ5~
CO HC
3~339
N0x
/^ftf J98"
ttfo
3/t> \//o,^?
3/V
ฃ/ <1C. ? !//O ^>/^
/# /
3%/
Quantity
Unit
/rfis; ,?69I To A/3
/?. OS/ 1 / ,^<&J . .-;#& l< Vf#s>.
ฃrfi?\ /V./oS1 \XVฃst/<,
3V?
W?& }ฃ
&ฃTP/
KGfiL
\
" i C> "^d I
ป(S.>ft-/ป '
^7/^1 I
/) -^ O/ / 'J
-------
PARTICULATE
SULFUR OXIDES
SOLID
WASTE
6%
OTHER
MOBLIE
7.3%
OTHER
MOBILE
10.9%
OTHER 11.7%
SOLID
WASTE
3.9%
-OTHER 5.5% ^COMMERCIAL
18.6%
HYDROCARBON
OTHER
MOBILE
7.1
CARBON MONOXIDE
GASOLINE
VEHICLES
58.9%
GASOLINE
VEHICLES
91.0%
-OTHER 1 .9%
PROCESS 14.6%
OTHER
MOBILE
13.5%
OTHER 4.9%
POWER PLANTS
59.8%
COMMERCIAL
21 .8%
NITROGEN OXIDES
OTHER 11 .7%
POWER
PLANTS
19.4%
COMMERCIAL 5.8%
INCLUDES INSTITUTIONAL & INDUSTRIAL FUEL
FIGURE 5,1 POLLUTANTS EMITTED BY PRINCIPAL SOURCES - KANSAS PORTION OF THE
-------
PARTICULATE
SULFUR OXIDES
COMMERCIAL 4.
OTHER
MOBILE
10.5%
OTHER
8.2%
POWER PLANTS 5.
SOLID WASTE 11.2%
HYDROCARBON
OTHER 10.6%
OTHER
MOBILE
5.8%
OTHER
7.7%
PROCESS 5.5%
SOLID WASTE 13.0%
CARBON MONOXIDE
RESIDENTIAL-
16.0%
OTHER 7.9%
POWER
PLANTS
45.9%
OTHER
MOBILE
8.4%
OTHER
11 .6
COMMERCIAL'
17.4%
OTHER MOBILE 12.8%
NITROGEN OXIDES
COMMERCIAL
2.2%
POWER PLANTS
19.9%
*INCLUDES INSTITUTIONAL & INDUSTRIAL FUEL
FIGURE 5,2 POLLUTANTS EMITTED BY-PRINCIPAL SOURCES - NORTHEAST
-------
PARTICULATE
SULFUR O.XIDES
SOLID
WASTE
7.5%
OTHER 9.7%
HYDROCARBON
GASOLINE
VEHICLES
62.5%
CARBON MONOXIDE
GASOLINE
VEHICLES
86.2%
RESIDENTIAL
7.7%
OTHER
MOBILE
7.6% OTHER 4.9%
COMMERCIAL 8.5%
OTHER
MOBILE 4.7%
OTHER 9.1%
PROCESS 11.5%
SOLID
WASTE 9.5%
OTHER
MOBILE 6.1%
OTHER 10.4%
INCLUDES INSTITUTIONAL & INDUSTRIAL FUEL
NITROGEN OXIDES
GASOLINE
VEHICLES
69.0%
COMMERCIAL
10.9%
POWER
PLANTS
2.8%
OTHER
MOBILE 11.3%
OTHER 6.0%
FIGURE 5,3 POLLUTANTS EMITTED BY PRINCIPAL SOURCES - NORTH CENTRAL
-------
PARTICULATE
SULFUR OXIDES
COMMERCIAL*?.4%
GASOLINE
VEHICLES
7.9%
OTHER 9.9%
HYDROCARBON
PROCESS 7.7%
GASOLINE
VEHICLES
70.
CARBON MONOXIDE
SOLID WASTE 10.6%
OTHER MOBILE 6.8%
OTHER 4.1%
OTHER 18.3%
OTHER
MOBILE
26.4%
OTHER
MOBILE 2.6%
OTHER 7.9%
RESIDENTIAL
21 .0%
POWER
PLANTS
7.7%
COMMERCIAL*
26.6%
NITROGEN OXIDES
COMMERCIAL
8.3%
GASOLINE
VEHICLES
65.1
POWER PLANTS
10.2%
OTHER
MOBILE
11.1%
OTHER
5.3%
INCLUDES INSTITUTIONAL & INDUSTRIAL FUEL
FIGURE 5,4 POLLUTANTS EMITTED BY PRINCIPAL SOURCES - NORTHWEST
-------
PARTICULATE
SULFUR OXIDES
OTHER 9.
OTHER
MOBILE
13.8%
SOLID WASTE 2.3%
OTHER 3.3%
CARBON MONOXIDE
SOLID WASTE 7.3%
HYDROCARBON
GASOLINE
VEHICLES
64.4%
PROCESS 7.9%
SOLID WASTE 10.1%
OTHER MOBILE 6,1%
OTHER 11.5%
GASOLINE
VEHICLES
86 .8%
OTHER MOBILE 2.
OTHER 3.9%
OMMERCIAL
30.6%
RESIDENTIAL
46.2%
NITROGEN OXIDES
COMMERCIAL 10.4%
POWER PLANTS
7.9%
OTHER
MOBILE.
9.4%
OTHER 8.3%
INCLUDES INSTITUTIONAL & INDUSTRIAL FUEL
FIGURE 5,5 POLLUTANTS EMITTED BY PRINCIPAL SOURCES - SOUTHEAST
-------
PARTICULATE
SULFUR OXIDES
COMMERCIAL 13.2%
OTHER 1.1%
RESIDENTIAL 5.4%
GASOLINE VEHICLES
4.2%
OTHER 11.3%
SOLID
WASTE
15.0%
CARBON MONOXIDE
HYDROCARBON
PROCESS 7.7%
SOLID WASTE
7.0%
GASOLINE
VEHICLES
91.9%
OTHER
MOBILE
14.2%
PROCESS
12.4%
GASOLINE VEHICLES
7.6%
RESIDENTIAL
5.4%
OTHER 1.2%
OTHER MOBILE 1.7%
SOLID WASTE 5.2%
NITROGEN OXIDES
OTHER MOBILE 6.3%
COMMERCIAL^.8%
OTHER 9.3%
PROCESS 12.1%
OTHER 2.5%
GASOLINE
VEHICLES
42.9%
POWER
LANTS
17.7%
OTHER
MOBILE
5.8%
COMMERCIAL 19.0%
INCLUDES INSTITUTIONAL & INDUSTRIAL FUEL
FIGURE 5,6 POLLUTANTS EMITTED BY PRINCIPAL SOURCES - SOUTH
-------
PARTICIPATE
SULFUR OXIDES
COMMERCIAL 7.5%
SOLID WASTE 13.4%
GASOLINE
VEHICLES 6.9%
HYDROCARBON
OTHER 4.1%
OTHER
6.8%
SOLID
WASTE
5.0%
GASOLINE
VEHICLES
54.9%
OTHER MOBILE
4.8%
OTHER
MOBILE
30.3%
OTHER
5.0%
GASOLINE VEHICLES
18.0%
CARBON MONOXIDE
GASOLINE
VEHICLES
92.6%
SOLID WASTE 4.5%
OTHER 2.9%
RESIDENTIAL
15.8%
COMMERCIAL*30.9%
NITROGEN OXIDES
COMMERCIAL
11.0%
POWER
PLANTS
12.3%
GASOLINE
VEHICLES
64.7%
OTHER 2.6%
OTHER
MOBILE 9
*INCLUDES INSTITUTIONAL & INDUSTRIAL FUEL
FIGURE 5,7 POLLUTANTS EMITTED BY PRINCIPAL SOURCES - SOUTHWEST
------- |