OCTOBER 1977
Regional
Air Pollution
Study
AMC7010.T0124FR
i
Rockwell International
Air Monitoring Center
11640 Administration Drive
Creve Coeur, Missouri (63141)
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OCTOBER 1977 AMC7010.T0124FR
REGIONAL AIR POLLUTION STUDY
(RAPS)
FINAL REPORT
FUGITIVE DUST SURVEY AND INVENTORY
TASK ORDER NO. 124
CONTRACT NO. 68-02-2093
Prepared for:
Environmental Protection Agency
Environmental Sciences Research Laboratory
Research Triangle Park, North Carolina 27711
by
Robert W. Griscom
Edward 0. Nelson
Fred E. Littman
Rockwell International
Atomics International Division
Air Monitoring Center
11640 Administration Dr.
Creve Coeur, Mo. 63141
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ABSTRACT
As part of the Regional Air Pollution Study, ten monitoring stations and
two special study sites were used to collect Hi-Vol particulate data. Nearby
ground-level fugitive dust sources can have a disproportionate effect on the
data collected at these sites. This report covers a site survey which was
conducted to assess the impact of ground-level fugitive dust sources within
a one mile radius of each site.
The areas surrounding RAMS stations 103, 105, 106, 108, 112, 115, 118,
120, 122 and 124, and the special Hi-Vol study sites on the Municipal Courts
building at 14th and Market, and next to City Air Monitoring Station No. 2
at S. Broadway and Hurck, were surveyed. An emissions inventory of fugitive
dust sources near these sites was assembled.
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CONTENTS
Abstract n
Figures in
Tables iij
1.0 Introduction 1
2.0 Site Survey 2
3.0 Emission Inventory 7
4.0 Emission Factors 11
5.0 Fugitive Dust Emission Calculations 14
References 15
Appendices
A. Site Survey - Station 103 16
B. Site Survey - Station 105 33
C. Site Survey - Station 106 51
D. Site Survey - Station 108 66
E. Site Survey - Station 112 83
F. Site Survey - Station 115 99
G. Site Survey - Station 118 116
H. Site Survey - Station 120 133
I. Site Survey - Station 122 149
J. Site Survey - Station 124 164
K. Site Survey - 14th and Market 179
L. Site Survey - S. Broadway and Hurck 195
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FIGURES
Number Page
1 Annular Ring Segments for Describing Location and Type
of Nearby Ground Level Activity 4
2 RAPS Monitoring Station Locations 5
3 Location of Special Hi-Vol Sites with Reference to
RAMS Sites 6
4 Map of Thornthwaite's Precipitation-Evaporation Index
Values for State Climatic Divisions 9
5 Soil Silt Content (%) for RAPS Grid System 10
TABLES
Number Page
1 Fugitive Dust Source Categories in the St. Louis
Study Area 7
m
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1.0 INTRODUCTION
In conjunction with the Regional Air Pollution Study (RAPS), ten of the
Regional Air Monitoring System (RAMS) stations were equipped with Hi-Vol
samplers and Lawrence Berkeley Laboratories (LBL) Dichotomous samplers to
measure particulate concentrations in the St. Louis area. The Hi-Vol filter
inlet was approximately 9 feet above ground level and the inlet for the
Dichotomous samplers was approximately 10 feet above ground. Recent studies
have indicated that nearby ground level sources can disproportionally
influence particulate concentrations measured with Hi-Vol samplers.
Therefore, it was deemed necessary that sources adjacent to the RAMS
stations be assessed to determine potential impact on the results obtained
at each station.
The fugitive dust inventory gathered for the RAPS study does not have
the resolution to adequately assess localized effects on a station. The
purpose of this study has been to complement the emission inventory by
conducting a site survey and a subsequent inventory of ground level fugitive
particulate sources within a one mile radious of each RAMS station containing
Hi-Vol and LBL aerosol samplers. In addition, two sites have been added
which were used as Hi-Vol sampling locations during intensive studies.
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2.0 SITE SURVEY
Each station in this study was visited and the surrounding area was
surveyed to determine the extent of any ground level fugitive dust sources.
The area within a one mile radius of each station was subdivided according
to Figure 1. The segments are numbered in Figure 1 and the surveys of each
site are discussed using the same numbering system. An emission inventory
of the ground level particulate sources was assembled for each site.
Black and white and color photographs of the area within a one-quarter
mile radius of each site were taken from a helicopter. A sketch was also
made of the area within a quarter mile radius. The black and white photo-
graphs, sketches, and an aerial map, are included with each survey report
(Figures 1 - 7) in the Appendices. One set of color photographs has been
submitted to the Project Officer.
The stations covered in this study are 103, 105, 106, 108, 112, 115,
118, 120, 122, and 124 in the RAMS network and two sites from a special
HI-Vol study, located at 14th and Market on the Municipal Courts building
and at S. Broadway and Hurck next to City Station No. 2. The locations of
the RAPS monitoring stations is shown in Figure 2. The locations of the two
special Hi-Vol sites are shown in Figure 3.
The locations of the stations in both longitude/latitude and UTM
(Zone 15) coordinates are given below:
UTM (ZONE 15)
SITE LATITUDE LONGITUDE NORTHING EASTING ELEVATION
RAMS
RAMS
RAMS
RAMS
RAMS
RAMS
103
105
106
108
112
115
N 38°
N 38°
N 38°
N 38°
N 38°
N 38°
39'
36'
36'
44-
38'
47'
29"
18"
59"
08"
52"
36"
W 90°
W 90°
W 90°
W 90°
W 90°
W 90°
09 '17"
12'05"
15'32"
08' 32"
18'43"
02 '23"
4,282
4,276
4,277
4,291
4,280
4,297
,467m
,453m
,566m
,102m
,913m
,799m
747,
743,
738,
748,
733,
757,
588m
706m
660m
407m
938m
Him
127m
131m
150m
130m
170m
134m
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UTM (ZONE 15)
SITE LATITUDE LONGITUDE NORTHING EASTING ELEVATION
RAMS 118
RAMS 120
RAMS 122
RAMS 124
14th and
Market
Broadway
& Hurck
N 38°
N 38°
N 39°
N 38°
N 38°
N 38°
29
41
04
14
37
32
'11"
44"
50"
'39"
'38"
'29"
W 90°
W 90°
W 90°
W 90°
W 90°
W 90°
12
26
12
09
12
15
'48"
'06"
'24"
'06"
06"
52"
4,263
4,285
4,329
4,236
4,278
4,269
,256m
,909m
,223m
,537m
,960m
,220m
743
723
741
749
743
738
,065m
,079m
,631m
,275m
,600m
,420m
155m
168m
180m
207m
160m
148m
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I 1/1 j 1/4 I
I mile I mile '
1/2
mile
FIGURE 1. ANNULAR RING SEGMENTS FOR DESCRIBING LOCATION AND TYPE OF
NEARBY GROUND LEVEL ACTIVITY.
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RAPS CENTRAL
RAMS STATIONS
FIGURE 2. RAPS MONITORING STATION LOCATIONS
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FIGURE 3. LOCATION OF SPECIAL HI-VOL SITES
WITH REFERENCE TO RAMS SITES
A - 14th and Market
B - S. Broadway and Hurck
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3.0 EMISSION INVENTORY
Each Hi-Vol site was surveyed for any nearby sources of fugitive dust.
The source categories in Table 1 are the types which constitute dust sources
in the St. Louis area.
TABLE 1. FUGITIVE DUST SOURCE CATEGORIES
IN THE ST. LOUIS STUDY AREA
Cleared Areas
Active Construction
Building construction
Highway construction
Playgrounds and athletic fields
Reentrained dust from paved streets
Normal streets
Commercial (dirty) streets
Unpaved roads
Railroad right-of-ways and yards
Agriculture
Tilling operations
Wind erosion
The emission rates from these sources are dependent upon several param-
eters, which include: soil type, wind speed, soil moisture, precipitation,
vegetative cover, and traffic. Emission factors have been developed by EPA
contractors which incorporate these emission parameters.(1) The study areas,
however, were Reno and Las Vegas, Nevada, and the factors which were
developed are most applicable for these two cities. They can, however, be
applied to the St. Louis area in a modified form. Emission factors for
cleared areas, playgrounds and athletic fields, and railroad right-of-ways
and yards have been used.in this RAPS site survey. These factors have been
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related to St. Louis through the use of the Thornthwaite's precipitation-
evaporation (P-E) index (2), which is calculated from the sum of 12 monthly
ratios of measured precipitation to measured evapo-transpiration. Empirical
data have shown that soil loss varies inversely as the square of the P-E
index. The P-E indices for the United States are shown in Figure 4. The
values for Reno, Nevada and St. Louis are 20 and 93, respectively. This
index yields a correction factor of
(||)2 =0.046
when applying emission factors for Reno in St. Louis.
Fugitive dust sources in the St. Louis area were also studied.(3) The
sources which were studied were unpaved roads, agriculture and construction.
The emission factors which were developed are directly applicable to this
site survey. Emissions from agricultural tilling have a significant effect
on several of the rural stations. The soil composition is a principal part
of the determination of the emission factor for agriculture. The silt
content of the soils in the St. Louis area is shown in Figure 5.
The fugitive dust generated by entrainment on paved roads has been
recently studied.(4) This new information differs from the values reported
in the PEDCO study and has been incorporated in this report since it is
more applicable to this site survey.
Emissions from fugitive sources within a one mile radius area around
each Hi-Vol site have been calculated using these references and are
included as appendices to each site survey. Significant point sources of
particulates are identified by their RAPS ID codes: e.g. 26-4280-03, for
Anheuser-Busch Brewery.
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FIGURE 4. MAP OF THORNTHWAITE'S PRECIPITATION-EVAPORATION INDEX
VALUES FOR STATE CLIMATIC DIVISIONS.
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i WASHINGTON
: 70
EF^ERSO_N
i *"
FIGURE 5. SOIL SILT CONTENT (%) FOR RAPS GRID SYSTEM
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4.0 EMISSION FACTORS
Cleared Areas
The factor chosen here is from the PEDCO report for Reno, Nevada. It
applies to a clay-loam soil with no vegetative cover and is corrected for
the P-E index:
0.24 ton/acre/year x 0.046 = 0.011 ton/acre/year
Active Construction
This factor is from the Midwest Research Institute report and is
dependent upon the duration of the construction effort:
1.0 ton/acre/month
Playgrounds and Athletic Fields
This factor is from the PEDCO report. Measured data are unavailable;
thus, a value is proposed for use which is greater than wind erosion from
cleared land and less than construction sites. Corrected for the P-E index,
it is:
1.50 ton/acre/year x 0.046 = 0.069 ton/acre/year
Reentrained Dust from Paved Streets
This factor has been furnished by EPA from an MRI study which has not
yet been published (EPA Publication No. AP-42, Sec. 11.2.5 (Draft), September
1977).
5 gm/vehicle miles traveled - clean streets
20 gm/vehicle miles traveled - dirty streets
Traffic data have been obtained from the most recently available county high-
way traffic maps. These vary from 1971 data to 1975 data. Mileage traveled
11
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is equal to the daily traffic count data times the length of the traffic
link in the area of study. The traffic count data apply to weekday traffic.
Traffic on weekends has been estimated by assuming that half the number of
vehicles travel on weekends. Therefore, annual data = daily data x (250
weekdays + 1/2 of 100 weekend days) or 300 x daily data.
Streets in St. Louis City are cleaned every two weeks, less frequently
in St. Louis County. This may have some short term effect on stations 105,
106, 112, 120, and the two special Hi-Vol sites. The effect has not been
evaluated.
Unpaved Roads
This factor is from the MRI report:
S_
0.49 s
r
r
30
d
365
pounds/vehicle miles traveled
where: sr = percent silt content of road surface material
S = average vehicle speed, miles per hour
d = number of dry days per year (average of 250 dry days in the
St. Louis study area)
Railroad right-of-ways and yards
This factor is from the PEDCO report for the Reno area, corrected for
the P-E index. It is based on the cleared land emission factor with the
additional assumptions of no vegetative cover, sandy soil, half the area
stabilized due to treatment with oil or chemicals, and train traffic in-
creasing the wind erosion emissions by 20 percent:
0.2 ton/acre/year x 0.046 = 0.0092 ton/acre/year
Agricultural Tilling
This factor is from the MRI study:
St
1.1 x- pounds/acre = 0.318 S. pounds/acre
(PE/50T
where: S. = silt content of soil, percent
PE = Precipitation - Evaporation Index, 93 for St. Louis
12
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Emissions determined using this factor are for each tilling operation.
Fields in the St. Louis area are tilled on the average of four equivalent
tillings per year considering primary and secondary tilling, planting, and
harvesting. These emissions are highly seasonal and occur principally in
the early spring. The silt content of the soils was obtained from Reference
3.
Hind Erosion of Tilled Land
This factor is from the MRI report. The threshold value of emissions
is 3.5 tons/acre/year when the surface winds exceed 12 mph. This condition
exists in St. Louis 26% of the time, thus:
3.5 tons/acre/year x 0.26 = 0.9 tons/acre/year
Agricultural land is vulnerable to wind erosion from the time of primary
tilling to one month after planting. This time varies from 3 to 7 months,
depending on the crop. Assuming an average time of 5 months, the wind
erosion factor for the St. Louis area becomes
5
0.9 tons/acre/year x = °-38 tons/acre/year
13
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5.0 FUGITIVE DUST EMISSION CALCULATIONS
The following formulas were used in calculating emissions. All emissions
are in tons per year.
1. Paved Roads
Emissions, (clean streets) = ADT x length (miles) x 1.65 x 10
(dirty streets) = ADT x length (miles) x 6.6 x 10"3
2. Unpaved Roads
Emissions = ADT x length (miles) x speed (miles/hour) x % silt content
x 5.6 x 10"6
3. Railroads
Emissions = area (acres) x 9.2 x 10
4. Agricultural Tilling
Emissions = area (acres) x % silt x 6.4 x 10"
5. Wind Erosion, Tilled Land
Emissions = area (acres) x 3.8 x 10
6. Playgrounds and Athletic Fields
_o
Emissions = area (acres) x 6.9 x 10"
7. Cleared Areas
_2
Emissions = area (acres) x 1.1 x 10
8. Active Construction
Emissions = area (acres) x time (month)
14
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REFERENCES
1. Nevada Particulate Control Study for Air Quality Maintenance Areas,
Task B Report, Factors Influencing Emissions From Fugitive Sources,
EPA Contract No. 68-02-1375, PEDCO - Environmental Specialists,
Cincinnati, Ohio, January 1976.
2. Thornthwaite, C. W., Climates of North America According to a New
Classification. Geograph. Rev. 21: 633-655, 1931.
3. Cowherd, Chatten and Christine Guenther, Development of a Methodology
and Emission Inventory for Fugitive Dust for the Regional Air Pollution
Study, EPA-450/3-76-003, Midwest Research Institute, Kansas City,
Missouri, January 1976.
4. Cowherd, Chatten and Christine Guenther, Quantification of Dust
Entrapment From Paved Roadways, EPA Contract No. 68-02-1403, Task
Order 25, Midwest Research Institute, Kansas City, Missouri (not yet
published).
15
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APPENDIX A
SITE SURVEY - STATION 103
16
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CONTENTS
A.I Site Survey - Station 103
A.1.1 Emissions
A.2 Fugitive Dust Emission Calculations
18
19
28
FIGURES
Number
A.I Quarter Mile Area Surrounding Station 103
A.2 Station 103 - Direction East
A.3 Station 103 - Direction-SW
A.4 Station 103 - Direction-NW
A.5 Station 103 - Direction-NE
A.6 Station 103 - Direction-South
A.7 Station 103 - Surrounding Area to One Mile
Page
21
22
23
24
25
26
27
Number
TABLES
A.I Fugitive Dust Emissions, Tons Per Year
Page
20
17
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A.I SITE SURVEY - STATION 103
Station 103 is located approximately 350 meters east of the small, old,
residential community of Brooklyn, Illinois and just over a mile north of
the National Stockyards operations. There are a few scattered industries in
the area, some highways and several railroad tracks and yards. Almost half
of the area is covered with small farms.
The immediate quarter mile is almost entirely farmland as shown in
Figure A.I. The road in front of the station is lightly used and carries
approximately 400 cars per day. The fields surrounding the station are
primarily used for growing wheat. The tip of the lake shown in Figure A.I
was dried up during the summer in 1976.
Segment 2:
Segment 2 contains the only two industrial plants which could have a
localized effect on station 103. The plants are next to each other in the
southern end of this segment. One plant, USS Agri Chem, manufactures
fertilizer utilizing waste and bone materials from the stockyards, and the
other plant, Conagra, manufactures dog food. As the photograph in Figure A.2
indicates, considerable dust is generated at times from these industries.
Data on these emissions are unavailable.
Segment 3:
Segment 3 is almost entirely composed of farmland with one road and one
rail line passing through it.
Segment 4:
Segment 4, shown in Figure A.3, is about one third farmland. There is a
small residential area, two roads, several rail lines and a railroad repair
shop operated by Terminal Railroad.
18
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Segment 5:
Segment 5 is more than half farmland with several rail lines.
Segment 6:
Segment 6 is the only segment with a sizeable road, Highway 203, which
carries 21,500 cars per day. Approximately half of the area is farmland.
The rest of the area is composed of part of Horseshoe Lake and railroad and
highway rights-of-way.
Segment 7:
Segment 7 is mostly farmland. The very southern section partially
covers the National Stockyards area. Some of the companies still operating
are Swift & Co., E. St. Louis Rendering, and Evans Products; none of which
contributes significantly to the fugitive dust loadings.
Segment 8:
Segment 8 is partially farmland and mostly rail yards. This segment
covers most of the residential community of Brooklyn.
Segment 9:
Segment 9 contains many rail yards, shown in Figure A.4, part of
Brooklyn, some farmland, and an automobile shipping parking lot. Approxi-
mately 3 miles to the north-northeast of this site is the Granite City
Steel Works which constitute a major particulate source in this area and
would undoubtedly affect the particulate loadings at station 103. The
steel works can be seen in the background of Figure A.5.
A.1.1 EMISSIONS
The calculations of the fugitive dust emissions in the area surrounding
station 103 are included as Section A.2. A summary of the emissions by
segment is shown in Table A.I. The principal source of emissions is agricul-
tural tilling and wind erosion from the exposed tilled land. These
emissions are highly seasonal, occurring principally in the spring. None
of the roads in this area are curbed.
19
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TABLE A.I FUGITIVE DUST EMISSIONS, TONS PER YEAR
Segment
1
2
3
4
5
6
7
8
9
Paved Roads
0.33
0.96
0.34
0.58
27.77
574.56*
6.22
3.04
Agriculture
Tilling
2.90
0.39
2.18
1.07
1.07
2.29
6.87
2.29
3.63
Wind Erosion
Tilled Land
28.84
3.91
21.60
10.64
10.64
22.80
68.40
22.80
36.10
Cleared
Land Rail Yards
0.06
0.43
0.02
0.11
0.21
0.44 0.03
0.08
0.55
0.57
*Unpaved
20
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FIGURE A.I QUARTER MILE AREA SURROUNDING STATION 103
21
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FIGURE A.2 STATION 103
DIRECTION EAST
22
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FIGURE A.3 STATION 103
DIRECTION - SW
23
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FIGURE A.4 STATION 103
DIRECTION - NW
24
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FIGURE A.5 STATION 103
DIRECTION - NE
25
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FIGURE A.6 STATION 103
DIRECTION - SOUTH
26
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FIGURE A.7 STATION 103
SURROUNDING AREA TO ONE MILE
1. Horseshoe Lake
2. USS Agri Chem
3. Conagra
4. Terminal Railroad Shop
5. Swift & Co.
6. National Stockyards
27
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A.2 FUGITIVE DUST EMISSION CALCULATIONS
SEGMENT 1:
Paved Roads:
Road
Bend Rd.
Railroad:
ADT
400
Agricultural Tilling:
% Silt
60
Wind Erosion, Tilled Land:
SEGMENT 2:
Paved Roads:
Road
Bend Rd.
Industrial St.
Total
Agricultural Tilling:
ADT
400
550
% Silt
60
Length (miles) Emissions (tpy)
0.5 0.33
Area (acres) Emissions (tpy)
6.8 0.06
Area (acres)
75.9
Area (acres)
75.9
Length (miles)
0.25
0.22
Area (acres)
10.3
Cleared Land: (Period when Horseshoe Lake dried up)
Area (acres)
38.8
Emissions (tpy)
2.90
Emissions (tpy)
28.84
Emissions (tpy)
.16
7g (dirty
street)
.94
Emissions (tpy)
.39
Emissions (tpy)
0.43
28
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Wind Erosion, Tilled Land:
SEGMENT 3:
Paved Roads:
Road
Industrial St.
Agricultural Tilling:
ADT
400
% Silt
60
Wind Erosion, Tilled Land:
Railroads:
SEGMENT 4:
Paved Roads:
Road
Bend Rd.
Industrial St.
Total
Agricultural Tilling:
ADT
900
400
% Silt
60
Wind Erosion, Tilled Land:
Railroads:
Area (acres) Emissions (tpy)
10.3 3.91
Length (miles)
0.51
Area (acres)
57.0
Area (acres)
57.0
Area (acres)
2.3
Length (miles)
0.32
0.15
Area (acres)
28
Area (acres)
28
Area (acres)
11.6
Emissions (tpy)
0.34
Emissions (tpy)
2.18
Emissions (tpy)
21.6
Emissions (tpy)
0.02
Emissions (tpy)
0.48
0.10
0.58
Emissions (tpy)
1.07
Emissions (tpy)
10.64
Emissions (tpy)
0.11
29
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SEGMENT 5:
Agricultural Tilling:
% Silt
60
Wind Erosion, Tilled Land:
Railroads:
SEGMENT 6:
Paved Roads:
Road
Bend Rd.
111. 203
Total
Agricultural Tilling:
ADT
1750
18800
% Silt
60
Wind Erosion, Tilled Land:
Railroads:
Cleared Land: (Horseshoe Lake)
Area (acres)
28
Area (acres)
28
Length (miles)
0.49
0.85
Area (acres)
3.8
Area (acres)
40
Emissions (tpy)
1.07
Emissions (tpy)
10.64
Area (acres) Emissions (tpy)
22.3 0.21
Emissions (tpy)
1.41
26.37
27.78
Area (acres) Emissions (tpy)
60 2.29
Area (acres) Emissions (tpy)
60 22.8
Emissions (tpy)
0.03
Emissions (tpy)
0.44
30
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SEGMENT 7:
Unpaved Roads:
Road
(Stockyard)
ADT Length (miles) Speed % Silt Emissions (tpy)
500 .57 20 60 574.56
Agricultural Tilling:
% Silt
60
Wind Erosion, Tilled Land:
Railroads:
SEGMENT 8:
Paved Roads:
Road
Bend Rd.
Industrial St.
Illinois 3
Total
Agricultural Tilling:
ADT
900
400
3000
% Silt
60
Hind Erosion, Tilled Land:
Railroads:
Area (acres) Emissions (tpy)
180
180
8.3
Length (miles)
0.17
0.28
1.17
Area (acres)
60
Area (acres)
60
Area (acres)
59.7
6.87
Area (acres) Emissions (tpy)
68.4
Area (acres) Emissions (tpy)
0.08
Emissions (tpy)
0.25
0.18
5.79
6.22
Emissions (tpy)
2.29
Emissions (tpy)
22.8
Emissions (tpy)
0.55
31
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SEGMENT 9:
Paved Roads:
Road
Illinois 3
Illinois 3 By Pass
Total
Agricultural Tilling:
ADT
2000
4150
Silt
60
Mind Erosion, Tilled Land:
Railroads:
Length (miles)
0.57
0.17
Area (acres)
95
Area (acres)
95
Emissions (tpy)
1.88
1.16
3.04
Emissions (tpy)
3.63
Emissions (tpy)
36.1
Area (acres) Emissions (tpy)
62-. 1 0.57
32
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APPENDIX B
SITE SURVEY - STATION 105
33
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CONTENTS
B.l Site Survey - Station 105 35
B.1.1 Emissions 38
B.2 Fugitive Dust Emission Calculations 47
FIGURES
Number Page
B.I Quarter Mile Area Surrounding Station 105 40
B.2 Station 105 - Direction-West 41
B.3 Station 105 - Direction-NW 42
B.4 Station 105 - Direction-East 43
B.5 Station 105 - Direction-South 44
B.6 Station 105 - Direction-WNW 45
B.7 Station 105 - Surrounding Area to One Mile 46
TABLES
Number Page
B.I Fugitive Dust Emissions, Tons Per Year 39
34
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B.I SITE SURVEY - STATION 105
t,
\
Station 105 is located on the eastern side of the parking lot of Fire
Station No. 11-16 of the St. Louis City Fire Department, situated on the
northeast corner of 7th Street and Shenandoah Avenue. Station 105 sits on
the Shenandoah side of the parking lot. The area in which the station is
located has heavy commercial-industrial activity. The commercial-industrial
activities are located primarily east of 7th Street with mostly residential
activities starting on the west side of the street and stretching westward.
The parking lot on which the station sits is paved and averages less than
20 vehicles per day.
The immediate quarter mile area surrounding the station is shown in
Figure B.I. The station is about 240 ft. east of 7th Street which averages
approximately 18,000 vehicles daily, excluding weekends and holidays.
There are no significant obstructions near the station. The Fire Station
is the nearest building to the site and is approximately 60 ft. away.
The Fire Station is a one story building with a gabled roof rising approxi-
mately 25 ft. to the apex of the roof (Figure B.2). To the immediate north
of the site a truck leasing agency has an office, parking lot and a repair
garage for large tractor type trucks. The repair garage is approximately
75 ft. away and about 20 ft. in height. The parking lot is paved and
averages from 20 to 100 vehicles per day. Stretching northward are several
commercial buildings with paved parking lots averaging from 20 to 100
vehicles per day. Broadway comes in from the north and terminates at
Russell Boulevard one block north of the station. Broadway, at this point,
averages approximately 2000 vehicles per day and Russell Boulevard averages
8800 vehicles per day. A paved parking lot to the northeast of the
station averages 20 to 100 vehicles per day. The area to the north is
shown in Figure B.3. The area directly to the east of the station is light
commercial. A truck body company occupies the building to the east-northeast
35
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with a small paved lot in the rear with an average volume of usage in
vehicles per day of 20 to 100. The easterly boundaries of the quarter mile
segment touches Monsanto Chemical's Queeny Plant, Figure B.4. The immediate
area south of the station is also commercial. A grassy lot is located
across Shenandoah to the southeast of the station. The area primarily to
the south consists of truck terminals. The truck terminal lots are paved
and vehicle usage is estimated to be 20 to 100 vehicles per day. Shenandoah
at this location is a lightly traveled street with an estimated average
of 200 vehicles per day. The area to the south is shown in Figure B.5. The
area west of the station is essentially residential in nature. The area
contains a church, grade school and a small park. All the parking lots in
this area are paved. The area to the west is shown in Figure B.6.
Segment 2:
Segment 2 is composed of commercial, industrial and residential property.
The residential property is again located primarily west of 7th Street and
the commercial and industrial property is located for the most part east of
7th Street. The commercial property is located primarily along the area
nearest 7th Street, the main thoroughfare through the segment. Monsanto
Chemical Company's Queeny Plant occupies most of the remaining area and is a
point source with the emission inventory reference number of 26-4280-23.
Located to the east of the Monsanto complex is the Missouri Pacific railroad
yards.
Segment 3:
This segment consists of a section of the Monsanto complex, manufacturing
plants, warehouses, portions of the Missouri Pacific railroad yards and truck
terminals. The Missouri Pacific railroad yards are located approximately
2200 ft. to the east-southeast. Manufacturing plants are located southeast
of the station and truck terminals to the south.
Segment 4:
Segment 4 consists primarily of trucking terminals, commercial interests
and some residential property. 7th Street passes through the central section
from northeast to southwest. Several parking lots are located in this
36
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segment but they are all paved. The residential property is again located
west of 7th Street.
Segment 5:
Segment 5 is mostly residential property. There are a few scattered
manufacturing plants in the segment but they are considered to be of little
consequence in the emission of particulates. Probably the largest con-
tributor to fugitive emissions is the interstate network of 1-44 and 1-55.
12th Street and Gravois Avenue are also contributors in this segment. The
Falstaff Brewing Company is located in the southern part of this segment.
Segment 6:
Commercial and industrial interests dominate in the area bounded by
Segment 6. Interstate highways, heavily traveled city streets and railroads
are located in this segment. The Mississippi River occupies about a third
of this segment. A large portion of the area on the river front is occupied
by railroad yards and warehouses. Many of the streets running in and around
the railroad tracks are not paved and are covered with gravel. Because the
railroad tracks pass through the area, traffic moves slowly. The manu-
facturing industry in this area is considered to contribute little to the
fugitive dust emissions. Along the river front are located several docks
where barge cargo may be handled. The barge cargo appears to be of the
type that would contribute little in the way of fugitive dust emissions.
There is a housing development construction site in the northern part of
this segment.
Segment 7:
Segment 7 has approximately 85% of its area taken up by the Mississippi
River. However, on the Illinois bank of the river is the Cahokia generating
plant, owned by the Union Electric Company. The Cahokia plant is listed as
a point source with the emission inventory reference number 14-6900-14. The
Missouri Pacific Railroad runs along the river front with a few freight and
warehouses.
37
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Segment 8:
Segment 8 is composed of commercial, industrial and residential
interests. 1-55 traverses the western portion of the segment from north to
south. 7th Street also passes through the segment from north to south.
Located in the central portion of the segment is the Anheuser-Busch Inc.
which is listed as a point source with an emission inventory reference
number of 26-4280-03. The southeastern part of the segment contains a
railroad yard.
Segment 9:
The Interstate exchange dominates this segment as a source for fugitive
dust emissions. 12th Street and Gravois Avenue are heavily traveled streets
in this segment and are also notable contributors. Most of the remainder of
the segment is made up of residential property.
B.I.I EMISSIONS
Fugitive dust emissions from sources within the one mile radius sur-
rounding station 105 have been calculated and are included in Section B.2.
Three point sources are located in the one mile radius and are listed by
reference number. Interstate highways, heavily traveled streets and rail-
roads play dominant roles in this area. The highways and streets are
normally plowed and salted during snowstorms. Table B.I presents the cal-
culated emissions in tabular form.
38
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TABLE B.I FUGITIVE DUST EMISSIONS, TONS PER YEAR
Playgrounds
Segment Paved Roads Ball Parks Railroads Construction
1 29.36 0.06
2 12.21 0.03
3 5.77 0.13
4 16.03 0.10
5 59.87
6 132.11 0.35 175.2
7 1.81 0.08
8 154.38 0.04
9 167.24
39
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N
FIGURE B.I QUARTER MILE AREA SURROUNDING STATION 105
40
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I " w « ii »
FIGURE B.2 STATION 105
DIRECTION - WEST
41
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FIGURE B.3 STATION 105
DIRECTION - NW
42
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FIGURE B.4 STATION 105
DIRECTION - EAST
43
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'^gf
te^ij
FIGURE B.5 STATION 105
DIRECTION - SOUTH
44
-------
FIGURE B.6 STATION 105
DIRECTION - WNW
45
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FIGURE B.7 STATION 105
SURROUNDING AREA TO ONE MILE
1. Monsanto 6. City Hospital
2. Anheuser-Busch Brewery 7. Housing Development Construction
3. Defense Mapping Agency 8. Nooter Boiler Works
4. Trucking Firms 9. Union Electric - Cahokia
5. Falstaff Brewery
46
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B.2 FUGITIVE DUST EMISSION CALCULATIONS
SEGMENT 1:
Paved Roads:
Road
7th Street
Broadway
Russell
2nd Street
3rd Street
Barton Street
Lami Street
Shenandoah
Pontiac Street
Allen Street
8th Street
9th Street
10th Street
Total
Playground:
SEGMENT 2:
Paved Roads:
Road
7th Street
Broadway
Geyer Street
2nd Street
3rd Street
Residential
Total
ADT
18010
2000
8810
2000
2000
4000
2000
3000
2000
3000
3000
5000
3000
ADT
18010
2000
2000
2000
2000
1000
Length (miles)
0.48
0.13
0.15
0.30
0.38
0.38
0.15
0.22
0.19
0.15
0.15
0.40
0.15
Area (acres)
.92
Length (miles)
0.25
0.25
0.43
0.11
0.24
0.84
Emissions (tpy)
14.26
0.43
2.18
0.99
1.25
2.50
0.50
1.09
0.63
0.74
0.74
3.30
0.74
29.35
Emissions (tpy)
.06
Emissions (tpy)
7.43
0.83
1.42
0.36
0.79
1.39
12.22
47
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Railroads:
SEGMENT 3:
Paved Roads:
Road
2nd Street
Barton Street
Kosciusko Street
Sidney Street
Dekalb Street
Total
Railroads:
SEGMENT 4:
Paved Roads:
Road
7th Street
Sidney Street
Lynch Street
Residential
Total
Playground:
Area (acres)
3.6
Emissions (tpy)
0.03
ADT
2000
4000
1000
5000
2000
ADT
18010
5000
2500
1000
Length (miles)
0. 30
0.19
0.30
0.20
0.42
Area (acres)
14.7
Length (miles)
0.26
0.51
0.27
1.81
Emissions (tpy)
0.99
1.25
0.50
1.65
1.39
5.78
Emissions (tpy)
0.13
Emissions (tpy)
7.73
4.20
1.11
2.99
16.03
Area (acres)
1.5
Emissions (tpy)
0.10
48
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SEGMENT 5:
Paved Roads:
Road
1-55
12th Street
Gravois Avenue
Russell Blvd.
Residential
Total
SEGMENT 6:
Paved Roads:
Road
1-55
Broadway
7th Street
12th Street
Park Avenue
Residential
Total
Railroads:
ADT
93180
18110
5100
11250
2830
1000
Active Construction:
ADT
93180
4900
12550
8810
1000
ADT
93180
18110
5100
11250
2830
1000
Length (miles)
0.30
0.48
0.11
0.27
2.22
Length (miles)
0.66
0.49
0.49
0.25
0.68
2.46
Emissions (tpy)
46.12
3.88
2.28
3.92
3.66
59.86
Emissions (tpy)
101.47
14.64
4.12
4.64
3.17
4.06
132.10
Time (month)
12
SEGMENT 7:
Paved Roads:
Road
Commercial
Railroads:
ADT
1000
Area (acres)
38.6
Area (acres)
14.6
Emissions (tpy)
0.36
Emissions (tpy)
175.2
Length (miles)
1.1
Area (acres)
9.2
Emissions (tpy)
1.81
Emissions (tpy)
0.08
49
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SEGMENT 8:
Paved Roads:
Road
1-55
Broadway
7th Street
Arsenal Street
Pestalozzi
Residential
Total
Railroads:
SEGMENT 9:
Paved Roads:
Road
1-55
1-44
Gravois Avenue
12th Street
Russell Blvd.
Park Avenue
Lafayette Ave.
14th Street
Residential
Total
ADT
80900
14470
3540
8970
4720
1000
ADT
80900
47160
20950
17450
6370
4760
8950
10970
1000
Length (miles)
0.83
0.49
0.49
0.87
0.91
5.5
Area (acres)
4.0
Length (miles)
0.45
0.53
0.64
0.42
0.49
0.42
0.57
0.39
4.73
Emissions (tpy)
110.79
11.69
2.86
12.87
7.09
9.08
154.38
Emissions (tpy)
0.04
Emissions (tpy)
60.07
41.24
22.12
12.09
5.15
3.29
8.42
7.06
7.80
167.24
50
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APPENDIX C
SITE SURVEY - STATION 106
51
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CONTENTS
C.I Site Survey - Station 106 53
C.I.I Emissions 55
C.2 Fugitive Dust Emission Calculations 63
FIGURES
Number Page
C.I Quarter Mile Area Surrounding Station 106 56
C.2 Station 106 - Direction-West 57
C.3 Station 106 - Direction-West 58
C.4 Station 106 - Direct!on-NW 59
C.5 Station 106 - Direction-East 60
C.6 Station 106 - Direction-SE 61
C.7 Station 106 - Surrounding Area to One Mile 62
TABLES
Number Page
C.I Fugitive Dust Emissions, Tons Per Year 55
52
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C.I SITE SURVEY - STATION 106
Station 106 is located on the grounds of the Missouri Botanical Gardens
(Shaw's Gardens) in the city of St. Louis, Missouri. The station sits
approximately 240 ft. east of Alfred Avenue. There are several deciduous
trees in the vicinity of the station with the closest being approximately
50 ft. to the east-northeast and about 50 ft. in height. Most of the tallest
trees in the vicinity of the station average 50 ft. in height. The Botanical
Gardens operates a heating plant approximately 30 ft. due south of the
station. The heating plant is used to supply heat to the surrounding hot
houses and is used only during the cold season. The stack is approximately
53 ft. in height. The fuel used in heating is oil. The heating plant is
seldom used and from actual observations little if any smoke has been seen
coming from the stack.
The immediate quarter mile area surrounding the station is shown in
Figure C.I and the photograph in Figure C.2. West of the station is an
area of multi-family residences, Figure C.3. North of the station is
Interstate 44 which runs east-west. The station is well shielded in this
direction by trees, as seen in Figure C.4. The Interstate carries 49,800
cars per day. East of the station is a parking lot for visitors to the
Botanical Gardens. Beyond this lot are single family residences, Figure C.5.
To the south of the station are the Botanical Gardens, Figure C.6. The
gardens are heavily wooded. Just at the edge of the quarter mile area to
the south is the location of the Japanese Gardens. This is a large,
man-made attraction in the Botanical Gardens. The Japanese Gardens area
was under construction during all of 1975 and part of 1976.
Segment 2:
Segment 2 is approximately half residential area. Interstate 44 cuts
through this segment. There are some commercial/industrial companies
located in the northern part of this segment along Vandeventer Road.
53
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Segment 3:
Segment 3 is about 75 percent residential. The remainder of the area
is in the Missouri Botanical Gardens.
Segment 4:
Segment 4 is about 50 percent residential. The northern section of
this segment contains an automotive dealer and some commercial/industrial
companies located along Vandeventer and Kingshighway. The southern area of
this segment is the southern end of the Missouri Botanical Gardens. This
part of the gardens is almost entirely occupied by the Japanese Gardens
which were under construction in 1975 and 1976.
Segment 5:
Segment 5 contains a section of Interstate 44. The rest of this
segment is occupied by commercial and industrial companies. A major source
of particulates, Banner Iron Works, is located in this area. This company
has a RAPS source code of 26-4280-59. The stack at Banner Iron Works is only
about 85 feet tall and could easily have an effect on station 106.
Segment 6:
Segment 6 is approximately equally composed of residential and com-
mercial/industrial areas. There are several heavily traveled commercial
streets. The commercial/industrial area is primarily used for warehousing
and shipping/receiving on rail lines. Interstate 44 passes through this
segment.
Segment 7:
Segment 7 is entirely composed of residential areas and Tower Grove
Park.
Segment 8:
Residential areas and Tower Grove Park cover 75 percent of segment 8.
The northern section of this segment is occupied by small commercial/indus-
trial companies. The Carpndolet Foundry is in this area; however, no sig-
54
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nificant emissions, were seen coming from this company. Their baghouses
seem to be very adequate. At the very limit of the one mile area from
station 106, to the south, is the American Can Co. (RAPS source 26-4280-01).
The principal emissions from here would be hydrocarbons.
Segment 9:
Segment 9 is about 75 percent occupied with commercial/industrial areas,
located along Kingshighway and Manchester Road. Interstate 44 passes
through this segment. There are no major point sources in this area.
C.I.I EMISSIONS
Fugitive dust emissions in the area surrounding station 106 have been
calculated and the calculations are included in Section C.2. A summary of
the emissions by segment is shown in Table C.I.
The principal source of fugitive dust emissions in this area is from
entrainment of dust on paved roads. Almost all of the streets in this area
are curbed. The station is heavily shielded by trees around the site,
primarily to the north of the station.
TABLE C.I FUGITIVE DUST EMISSIONS, TONS PER YEAR
Segment
1
2
3
4
5
6
7
8
9
Paved Roads
45.16
32.90
5.86
12.27
35.56
70.66
14.20
62.59
107.35
Construction
5.22
82.60
55
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N
FIGURE C.I QUARTER MILE AREA SURROUNDING STATION 106
56
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*
FIGURE C.2 STATION 106
DIRECTION - WEST
57
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FIGURE C.3 STATION 106
DIRECTION - WEST
58
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.;
FIGURE C.4 STATION 106
DIRECTION - NW
59
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FIGURE C.5 STATION 106
DIRECTION - EAST
60
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FIGURE C.6 STATION 106
DIRECTION - SE
61
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FIGURE C.7 STATION 106
SURROUNDING AREA TO ONE MILE
1. Climatron
2. Japanese Gardens
3. Tower Grove Park
4. American Can Co.
5. Carondolet Foundry
6. Banner Iron Works
7. Warehousing
8. O'Fallon Technical School
-------
C.2 FUGITIVE DUST EMISSION CALCULATIONS
SEGMENT 1:
Paved Roads:
Road
Tower Grove Ave.
Vandeventer
1-44
Residential
Commercial
Total
Active Construction:
SEGMENT 2:
Paved Roads:
Road
1-44
Vandeventer
Tower Grove
Residential
Total
SEGMENT 3:
Paved Roads:
Road
Tower Grove
Residential
Total
ADT
12030
15160
49800
500
3000
Time (month)
12
ADT
49300
13930
10730
500
ADT
12030
500
Length (miles)
0.40
0.34
0.32
1.14
0.30
Area (acres)
0.46
Length (miles)
0.27
0.23
0.25
1.23
Length (miles)
0.23
1.57
Emissions (tpy)
7.94
8.50
26.29
0.94
1.48
45.15
Emissions (tpy)
5.52
Emissions (tpy)
22.18
5.29
4.43
1.01
32.91
Emissions (tpy)
4.56
1.30
5.86
63
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SEGMENT 4:
Paved Roads:
Road
Vandeventer
Kingshighway
Residential
Total
Active Construction:
SEGMENT 5:
Paved Roads:
Road
1-44
Kingshighway
Commercial
Total
SEGMENT 6:
Paved Roads:
Road
1-44
Vandeventer
Tower Grove
Manchester
Residential
Commercial
Total
ADT
15160
28860
500
Time (month)
12
ADT
49800
28860
3000
ADT
49800
12210
7200
9000
500
3000
Length (miles)
0.25
0.11
0.95
Area (acres)
6.9
Length (miles)
0.27
0.23
0.49
Length (miles)
0.50
0.50
0.34
0.44
3.20
1.27
Emissions (tpy)
6.25
5.23
0.78
12.26
Emissions (tpy)
82.60
Emissions (tpy)
22.19
10.95
2.42
35.56
Emissions (tpy)
41.08
10.07
4.04
6.53
2.64
6.28
70.64
64
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SEGMENT 7:
Paved Roads:
Road
Residential
Arsenal
Total
SEGMENT 8:
Paved Roads:
Road
Arsenal
Kingshighway
Southwest
Residential
Commercial
Total
SEGMENT 9:
Paved Roads:
Road
1-44
Kingshighway
Manchester
Residential
Commercial
Total
ADT
500
12520
ADT
14710
30280
12910
500
3000
ADT
49800
40100
13300
500
3000
Length (miles)
5.95
0.45
Length (miles)
0.50
0.68
0.49
2.77
0.76
Length (miles)
0.50
0.64
0.78
1.89
1.06
Emissions (tpy)
4.91
9.30
14.21
Emissions (tpy)
12.14
33.97
10.44
2.28
3.76
62.59
Emissions (tpy)
41.08
42.35
17.12
1.56
5.25
107.36
65
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APPENDIX D
SITE SURVEY - STATION 108
66
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CONTENTS
D.I Site Survey - Station 108 68
D.I.I Emissions 70
D.2 Fugitive Dust Emission Calculations 79
FIGURES
Number Page
D.I Quarter Mile Area Surrounding Station 108 72
D.2 Station 108 - Direction-West 73
D.3 Station 108 - Direct!on-SE 74
D.4 Station 108 - Direction-SW 75
D.5 Station 108 - Direction-NW 76
D.6 Station 108 - Direction-NE 77
D.7 Station 108 - Surrounding Area to One Mile 78
TABLES
Number Page
D.I Fugitive Dust Emissions, Tons Per Year 71
67
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D.I SITE SURVEY - STATION 108
Station 108 is located on the Roman farm in Madison County, Illinois on
the north side of Pontoon Road approximately 1000 feet west of Federal-Aid
Primary Route 151 and 2000 feet west of Illinois State Highway 3. The site
sits in an agricultural area where the farm land is cultivated right up to
the fence surrounding the site on the north, east and west. The southern
side of the station is located on Pontoon Road. The quarter mile area
surrounding the station is shown in Figure D.I.
Station 108 is situated along Pontoon Road which averages 300 vehicles
per day. Federal Aid-Primary Route 151 runs roughly northeast to southwest
and averages 3450 vehicles per day. The closest approach of FAP 151 to
108 is approximately 600 feet. An abandoned barn is located 640 feet to
the east of the site, Figure D.2. Cultivated farmland is located adjacent to
the station on the east and the crops are rotated yearly between wheat and
soybeans. The area immediately south of the station and across Pontoon Road
is cultivated farmland. FAP 151, to the southeast is approximately 800 feet
from the station, Figure D.3. The area southwest to west of the station is
entirely cultivated farmland, Figure D.4. Cultivated farmland is located
immediately west of the station with a farmhouse approximately 800 feet away.
The area northwest of the station is entirely farmland, Figure D.5. From
north to northeast of the station the area is cultivated farmland, Figure D.6.
Segment 2:
The area comprising this segment is almost entirely cultivated farmland.
The north central area has a narrow band of woodland passing through it.
FAP 151 passes through the lower right-hand section and also a short length
of Illinois State Highway 3. A narrow one lane unpaved farm road leads to a
farmhouse from Pontoon Road. The road is very lightly used and is not con-
sidered a significant source of fugitive dust.
68
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Segment 3:
This segment contains a portion of FAP 151 in the upper left-hand
corner. Illinois State Highway 3 traverses the segment from the upper
right-hand corner to the lower right-hand corner for a distance of approxi-
mately 2400 feet. The Illinois Terminal railroad tracks run parallel to
Illinois State Highway 3 on the east side of the railroad tracks. The
tracks are lightly used and seem to serve primarily for railroad car
storage. The railroad is not considered a significant source of fugitive
dust. Illinois State Highway 3 carries approximately 7400 vehicles per day
at this point. Pontoon Road crosses the central portion of this segment
and carries approximately 6300 vehicles per day at this point. Except for
two or three residential and a small commercial building the rest of the
area is cultivated farmland.
Segment 4:
Segment 4 is entirely cultivated farmland with the exception of FAP 151
which runs through the lower central portion and Old Rock Road that runs
through a small section of the upper left-hand corner. The name of the
county road was not available.
Segment 5:
Segment 5 is composed of vegetated fields and woodland along the upper
left-hand perimeter. A small finger of woodland protrudes into the central
region approximately 200 feet. Pontoon Road runs into the lower left-hand
section and terminates at the intersection with the Old Rock Road mentioned
in segment 4. Old Rock Road traverses the central section from the bottom
perimeter to the upper left-hand corner. The remainder of the segment is
made up of cultivated farmland.
Segment 6:
A drainage ditch with trees along each bank runs through the central
portion of segment 6. The farm road through segments 1 and 2 runs through
this segment. Vehicular travel on this road serves the farmhouses in these
sections and is minimal, fugitive dust from this road is considered to be
69
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negligible. FAP 151 joins Illinois State Highway 3 in this segment and runs
from the lower left-hand corner to the central right perimeter. The Illinois
Terminal Railroad has a roadbed running parallel to and on the east side of
FAP 151 and Illinois State Highway 3. The railroad is seldom used and is
used primarily for railroad car storage and is therefore not considered as a
significant source of fugitive dust.
Segment 7:
The upper right-hand section of this segment contains a residential
neighborhood belonging to Nameoki, Illinois. Pontoon Road runs through the
upper central region. The Gulf Mobile and Ohio, Burlington and Northern
Railroads have sections of roadbed through the segment and these sections
see quite a lot of activity and can be considered a significant source of
fugitive dust. Illinois Highway 3 also runs through the lower left-hand
corner with the Illinois Terminal Railroad running parallel on the east side.
A commercial area is located in the lower left section but is not considered
to be a significant source of fugitive dust. The remainder of the segment is
made up of cultivated farmland.
Segment 8:
The lower right-hand section of segment 8 contains part of the com-
mercial area contained in segment 7. FAP 151 runs through the central sec-
tion. There are several residential houses on either side of Old Rock Road
through the upper central section. The Chain of Rocks Canal passes through
the upper portion of the segment with a road running parallel to the canal
but has less than 75 vehicles per day.
Segment 9:
The Chain of Rocks Canal occupies a large portion of this segment.
Vegetated fields and woodland occupies most of the area east of the canal.
Cultivated farmland in this segment is found mostly on the western side of
the canal.
D.I.I EMISSIONS
Fugitive dust emissions from sources within the one mile radius
70
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surrounding station 108 have been calculated and are included in section D.2.
The highways in Illinois are usually plowed during snowstorms in this area.
Primary sources of fugitive dust are considered to be primarily from culti-
vated farmland, paved roads and railroads. The calculated emissions are
presented in tabular form in Table D.I.
TABLE D.I FUGITIVE DUST EMISSIONS, TONS PER YEAR
Segment
1
2
3
4
5
6
7
8
9
Paved Roads
2.67
1.29
7.52
1.85
0.24
9.89
12.13
3.19
Agricultural
Tilling
2.73
2.17
2.15
2.29
1.84
9.07
5.23
3.21
2.11
Wind Erosion
Tilled Land
40.54
32.26
32.00
34.01
27.36
134.60
77.71
47.73
31.38
71
-------
N
FIGURE D.I QUARTER MILE AREA SURROUNDING STATION 108
72
-------
FIGURE D.2 STATION 108
DIRECTION - WEST
Arrow indicates station site.
73
-------
FIGURE D.3 STATION 108
DIRECTION - SE
Arrow indicates station site,
74
-------
FIGURE D.4 STATION 108
DIRECTION - SW
Arrow indicates station site,
75
-------
FIGURE D.5 STATION 108
DIRECTION - NW
Arrow indicates station site.
76
-------
FIGURE D.6 STATION 108
DIRECTION - NE
Arrow indicates station site.
77
-------
FIGURE D.7 STATION 108
SURROUNDING AREA TO ONE MILE
1. A. 0. Smith
2. Chain of Rocks Canal
3. Federal Aid Primary Route 151
4. Illinois Highway 3
78
-------
D.2 FUGITIVE DUST EMISSION CALCULATIONS
SEGMENT 1:
Paved Roads:
Road
Sec. 1 Federal Aid
Primary 151
Sec. 2 Federal Aid
Primary 151
Sec. 1 Pontoon Road
Sec. 2 Pontoon Road
Total
Agricultural Tilling:
ADT
3450
4100
300
1250
% Silt
40
Length (miles)
0.23
0.14
0.39
0.11
Area (acres)
106.7
Emissions
1.31
0.95
0.19
0.23
2.68
Emissions
2.73
Wind Erosion. Tilled Land:
Area (acres)
106.7
SEGMENT 2:
Paved Roads:
Road ADT
Federal Aid Primary 151 3450
Illinois 3 7400
Total
Length (miles)
0.12
0.05
Agricultural Tilling:
% Silt
40
Wind Erosion, Tilled Land:
Area (acres)
84.9
Area (acres)
84.2
Emissions (tpy)
40.54
Emissions (tpy)
0.68
0.61
1.29
Emissions (tpy)
2.17
Emissions (tpy)
32.00
79
-------
SEGMENT 3:
Paved Roads:
Road
Federal Aid Primary 151
Sec. 1 Illinois State
Highway 3
Sec. 2 Illinois State
Highway 3
Sec. 1 Pontoon Road
Sec. 2 Pontoon Road
Total
Agricultural Tilling:
ADT Length (miles)
3450 0.19
7400 0.27
6800
1250
6300
0.18
0.19
0.07
% Silt
40
Wind Erosion, Tilled Land:
SEGMENT 4:
Paved Roads:
Road ADT
Federal Aid Primary 151 4100
Old Rock Road 75
Total
Agricultural Tilling:
% Silt
40
Wind Erosion, Tilled Land:
Area (acres)
84.2
Area (acres)
84.2
Length (miles)
0.27
0.19
Area (acres)
89.5
Area (acres)
89.5
Emissions (tpy)
1.08
3.30
2.02
0.39
0.73
7.52
Emissions (tpy)
2.15
Emissions (tpy)
32.00
Emissions (tpy)
1.83
0.02
1.85
Emissions (tpy)
2.29
Emissions (tpy)
34.01
80
-------
SEGMENT 5:
Paved Roads:
Road
Pontoon Road
Sec. 1 Old Rock Road
Sec. 2 Old Rock Road
Total
Agricultural Tilling:
ADT
300
275
75
% Silt
40
Wind Erosion, Tilled Land:
SEGMENT 6:
Paved Roads:
Road ADT
Federal Aid Primary 151 10900
Agricultural Tilling:
% Silt
50
Wind Erosion, Tilled Land:
SEGMENT 7:
Paved Roads:
Road
Illinois 3
Pontoon Road
Total
Agricultural Tilling:
ADT
6800
6300
Length (miles)
0.11
0.38
0.14
Area (acres)
72
Area (acres)
72
Length (miles)
0.55
Area (acres)
354.2
Area (acres)
354.2
Silt
40
Length (miles)
0.59
0.53
Area (acres)
204.5
Emissions (tpy)
0.05
0.17
0.01
0.23
Emissions (tpy)
1.84
Emissions (tpy)
27.36
Emissions (tpy)
9.89
Emissions (tpy)
9.07
Emissions (tpy)
134.60
Emissions (tpy)
6.62
5.51
12.13
Emissions (tpy)
5.23
81
-------
Wind Erosion, Tilled Land:
SEGMENT 8:
Paved Roads:
Road ADT
Federal Aid Primary 151 4100
Old Rock Road 75
Total
Agricultural Tilling:
% Silt
40
Wind Erosion, Tilled Land:
SEGMENT 9:
Agricultural Tilling:
% Silt
40
Wind Erosion, Tilled Land:
Area (acres) Emissions (tpy)
204.5 77.71
Length (miles)
0.49
0.56
Area (acres)
125.6
Area (acres)
125.6
Area (acres)
82.6
Area (acres)
82.6
Emissions (tpy)
3.13
0.06
3.19
Emissions (tpy)
3.21
Emissions (tpy)
47.73
Emissions (tpy)
2.11
Emissions (tpy)
31.38
82
-------
APPENDIX E
SITE SURVEY - STATION 112
83
-------
CONTENTS
E.I Site Survey - Station 112
E.I.I Emissions
E.2 Fugitive Dust Emission Calculations
85
87
96
FIGURES
i
Number
E.I Quarter Mile Area Surrounding Station 112
E.2 Station 112 - Direction-West
E.3 Station 112 - Direction-North
E.4 Station 112 - Direction-East
E.5 Station 112 - Direction-South
E.6 Station 112 - Direction-West
E.7 Station 112 - Surrounding Area to One Mile
Page
89
90
91
92
93
94
95
Number
TABLES
E.I Fugitive Dust Emissions, Tons Per Year
Page
84
-------
E.I SITE SURVEY - STATION 112
Station 112 is located in St. Louis County, Missouri on the campus of
Washington University, approximately 7 miles west of downtown St. Louis.
The station sits just inside the east gate of the Washington University
football field. A fairly large tree, approximately 50 feet high, is ojily
fifteen feet north of the station. This deciduous tree would definitely
screen the station from the north.
The immediate quarter mile area surrounding the station is shown in
Figure E.I and the photograph in Figure E.2. The football stadium is on the
western edge of the Washington University campus. The street right in
front of the station, on the east side, is strictly a driveway to the
parking lot along the north side of the football field, as seen in Figure
E.3. To the east of the station is a baseball field, shown in Figure E.4.
This is the only dirt, or unvegetated field in the area. All other fields
are grass covered. Beyond the baseball field, to the east and north, is
the main campus area. To the south of the station is Forsyth Blvd. running
east-west, and campus and residential housing, as shown in Figure E.5.
The football field west of the station, shown in Figure E.6, is used by the
University football team and the St. Louis Soccer Stars, a professional
soccer team. This field is grass covered and surrounded by a cinder track.
Dust is likely to be stirred up when the track is in use for track and
field events and university athletic programs.
The main streets in this area are Forsyth Blvd., Big Bend Blvd. which
runs north-south and is just west of the football field, and Forest Park
Parkway which is the northern boundary of Washington University. All of
the streets in this area are curbed and tree lined. With the exception of
the baseball field and the cinder track, the station is heavily shielded
from local fugitive dust sources by the deciduous trees in the area.
According to Highway Department Traffic Maps, Forsyth Blvd. carries 11300
85
-------
cars per day. Big Bend carries 11590 cars per day, and Forest Park Parkway
carries 18240 cars per day.
Segment 2:
Segment 2 is principally a residential area with high density single
family residences. The northeast quarter of Washington University is in
this segment. This part of the University is the location of the powerhouse
which burns coal and natural gas (RAPS Point Source 26-4300-16) and part of
the main parking lot which holds approximately 150 cars during school hours.
A section of the Forest Park Parkway passes through this segment.
Segment 3:
Segment 3 is mostly a residential area. The southeast quarter of
Washington University is included in this segment. This includes several
parking areas which hold approximately 500 cars during school hours.
Segment 4:
Segment 4 is approximately 60 percent covered by an area of very low
density, expensive single family dwellings. This area includes about half of
Fontbonne College. Big Bend Blvd. and Wydown Blvd. are the principal streets
in this segment. The rest of the area is residential.
Segment 5:
Segment 5 is almost entirely comprised of medium and high density
single family residences. Forest Park Parkway passes through this segment.
Segment 6:
Segment 6 is approximately half and half composed of residential and
commercial areas. The downtown, central business district of University
City is included in this area. There are no significant dust sources in the
commercial area. Approximately 70 percent of the area is comprised of
single and multi-family residences. Only about half of the area has any
tree lined streets, however the close packed housing serves the same
purpose. Several parking lots are located in this segment which hold
500-1000 cars. The principal street in this area is Delmar Blvd.
86
-------
Segment 7:
Segment 7 is composed of single and multi-family residences and a
section of Forest Park which is devoted to a golf course. The principal
street in this area is Skinker Blvd., running north-south. The main part
of the Concordia Seminary campus is in this segment.
Segment 8:
Segment 8 is about 75 percent composed of residential areas. A short
commercial section along Clayton Road is included in this segment. The
principal streets are Big Bend Blvd., Clayton Road, and a very short section
of the Forest Park Parkway.
Segment 9:
Segment 9 is almost entirely composed of residential areas. There is
a three block section of the Clayton business district with a department
store and parking for several hundred cars, almost a mile west of station
112, along the Forest Park Parkway.
E.I.I EMISSIONS
The calculation of the fugitive dust emissions in the area surrounding
station 112 are included in Section E.2. A summary of the emissions by
segment is shown in Table E.I.
The only significant source of fugitive dust in this area is from re-
entrainment of dust from paved roads. The amount of dust indicated in
Table E.I is undoubtedly greatly reduced by the curbed streets and the
abundance of trees which border most of the streets in this area. This is
a long established area of town and the deciduous trees range in height to
50 or 50 feet.
The baseball field to the east and the cinder track to the west may
constitute significant sources due to their proximity to the station during
a sporting event.
87
-------
TABLE E.I FUGITIVE DUST EMISSIONS, TONS PER YEAR
Segment Paved Roads Athletic Fields
1 25.19 0.09
2 11.45
3 7.77
4 12.12
5 16.86
6 77.68
7 52.16
8 31.98
9 48.24
88
-------
Intramural Fields
Dnive|psi+v | Housing j ")
FIGURE E.I QUARTER MILE AREA SURROUNDING STATION 112
89
-------
FIGURE E.2 STATION 112
DIRECTION - WEST
90
-------
FIGURE E.3 STATION 112
DIRECTION - NORTH
91
-------
FIGURE E.4 STATION 112
DIRECTION - EAST
92
-------
FIGURE E.5 STATION 112
DIRECTION - SOUTH
93
-------
FIGURE E.6 STATION 112
DIRECTION - WEST
94
-------
FIGURE E.7 STATION 112
SURROUNDING AREA TO ONE MILE
1. Washington University Admin. Bldg. 4.
2. Fontbonne College 5.
3. Forest Park 6.
University City - City Hall
Department Store
Concordia Seminary
95
-------
E.2 FUGITIVE DUST EMISSION CALCULATIONS
SEGMENT 1:
Paved Roads:
Road
Forsyth Blvd.
Big Bend Blvd.
Forest Park Parkway
Maryland Ave.
Lindell Blvd.
Parking lot driveway
Total
Playgrounds & Athletic
SEGMENT 2:
Paved Roads:
Road
Forest Park Parkway
Residential
Westgate Dr.
Total
SEGMENT 3:
Paved Roads:
Road
Forsyth Blvd.
Wydown Blvd.
Residential
ADT
11300
11590
18240
1500
1500
3000
Fields:
ADT
18240
500
3000
ADT
11300
3000
500
Length (miles)
0.47
0.38
0.27
0.08
0.08
0.13
Area (acres)
1.3
Length (miles)
0.30
1.67
0.21
Length (miles)
0.25
0.47
0.95
Emissions (tpy)
8.76
7.27
8.12
0.20
0.20
0.64
25.19
Emissions (tpy)
0.09
Emissions (tpy)
9.03
1.38
1.04
11.45
Emissions (tpy)
4.66
2.33
0.78
Total
7.77
96
-------
SEGMENT 4:
Paved Roads:
Road
Big Bend Blvd.
Forsyth Blvd.
Wydown Blvd.
Residential
Total
SEGMENT 5:
Paved Roads:
Road
Forest Park Parkway
Big Bend Blvd.
Residential
Total
SEGMENT 6:
Paved Roads:
Road
Forest Park Parkway
Skinker Blvd.
Delmar Blvd.
Commercial Sts.
Residential Sts.
Total
SEGMENT 7:
Paved Roads:
Road
Skinker Blvd.
Commercial Sts.
Residential Sts.
Clayton Rd.
ADT
11590
11300
3000
500
ADT
18780
10000
500
ADT
18240
26930
16200
5000
500
ADT
32160
3000
500
10000
Length (miles)
0.28
0.25
0.38
0.27
Length (miles)
0.34
0.28
2.06
Length (miles)
0.47
0.70
0.85
0.76
4.17
Length (miles)
0.85
0.38
3.28
0.15
Emissions (tpy)
5.35
4.66
1.88
0.22
12.11
Emissions (tpy)
10.53
4.62
1.70
16.85
Emissions (tpy)
14.15
31.10
22.72
6.27
3.44
77.68
Emissions (tpy)
45.10
1.88
2.70
2.47
Total
52.15
97
-------
SEGMENT 8:
Paved Roads:
Road
Clayton Road
Big Bend Blvd.
Wydown Blvd.
Forest Park Parkway
Residential
Forsyth Blvd.
Total
SEGMENT 9:
Paved Roads:
Road
Forest Park Parkway
Forsyth Blvd.
Delmar Blvd.
Pennsylvania Ave.
Midland Blvd.
Residential Sts.
Total
ADT
10000
15010
3000
20000
500
11300
ADT
19000
18740
11840
5050
9320
500
Length (miles)
0.40
0.49
0.57
0.11
3.03
0.27
Length (miles)
0.57
0.23
0.72
0.34
0.21
3.79
Emissions (tpy)
6.60
11.39
2.82
3.63
2.50
5.03
31.97
Emissions (tpy)
17.87
7.11
14.06
2.83
3.23
3.13
48.23
98
-------
APPENDIX F
SITE SURVEY - STATION 115
99
-------
CONTENTS
F.I Site Survey - Station 115 101
F.I.I Emissions 103
F.2 Fugitive Dust Emission Calculations 111
FIGURES
Number Page
F.I Quarter Mile Area Surrounding Station 115 104
F.2 Station 115 - Direction-North 105
F.3 Station 115 - Direction-North 106
F.4 Station 115 - Direction-NE 107
F.5 Station 115 - Direction-West 108
F.6 Station 115 - Direction-South 109
F.7 Station 115 - Surrounding Area to One Mile 110
TABLES
Number Page
F.I Fugitive Dust Emissions, Tons Per Year 103
100
-------
F.I SITE SURVEY - STATION 115
Station 115 is located in Madison County, Illinois, 4.5 miles southeast
of Edwardsville, Illinois, and approximately 14.5 mile northeast of downtown
St. Louis. The area surrounding the station is almost entirely farmland.
There are no significant obstructions near the station. The nearest objects
are trees to the east, approximately 300 feet.
The immediate quarter mile area surrounding the station is shown in
Figure F.I and the photograph in Figure F.2. This area is the principal
area of the community of Poag, Illinois. There are approximately twenty
houses in segment 1. About 50 percent of this area is in cropland. As
seen in Figure F.3, the station sits alongside Poag Road in a farmer's
field. This farm is used for growing melons, whereas most of the other
farms in the area are planted with corn, soybeans and wheat. Poag Road
runs east-west through this area and intersects County Highway 19, which
runs north-south. This intersection is seen in Figure F.4. According to
Illinois Highway Maps, dated 1971, Poag Road carries 425 cars per day west
of Poag and 800 cars per day east of Poag and Highway 19 carries 850 cars
per day north of Poag. Since that time a new highway has been started
which is currently under construction. This construction runs east-west
through segments 2, 5, 6 and 9 and can be seen in Figure F.2. Additional
traffic along Poag Road and Highway 19 is estimated as 100 cars per day on
each road link. Finally, there is a railroad line running NE to SW through
segment 1 as well as 2, 4, 6, and 8. The rail line is seen in the back-
ground of Figure F.5.
Segment 2:
Segment 2 contains a short section of the new highway construction.
Cropland makes up approximately 70 percent of this area. There are also
sections of Poag Road and Highway 19 in this segment.
101
-------
Segment 3:
Segment 3 contains sections of Highway 19 and another rural road.
There is some housing and approximately 70 percent of the area is in crop-
land.
Segment 4:
Segment 4 contains short sections of Poag Road and the railroad tracks.
Approximately 95 percent of the area is in cropland.
Segment 5;
Segment 5 contains a short section of the new highway construction.
Approximately 70 percent of the area is in cropland.
Segment 6:
Segment 6 contains approximately a 3/4 mile stretch of the new highway
construction. There are sections of Poag Road and Highway 19 in this segment.
In the northern part of this segment there is a diversion channel which
carries some water and is heavily vegetated on the banks. Just south of
this channel there is a service road which is little used and is estimated
to carry 25 cars per day. This service road is an unpaved road. Cropland
makes up about 60 percent of this area.
Segment 7:
Segment 7 contains a mobile home park with 65 units. Highway 19 runs
through this segment. Cropland makes up about 80 percent of this area.
Segment 8:
Segment 8 contains part of Poag Road and the railroad tracks. There
is also a small stretch of an unmarked road running north-south which carries
approximately 75 cars per day and is unpaved. Cropland makes up about 95
percent of the area.
Segment 9:
Segment 9 contains a 3/4 mile section of the new highway construction.
The diversion channel and service road are also located in this segment.
102
-------
There is also a small stretch of the unmarked road from segment 8. Cropland
makes up about 70 percent of this area.
F.1.1 EMISSIONS
The calculations of the fugitive dust emissions in the area surrounding
station 115 are included in Section F.2. A summary of the emissions by
segment is shown in Table F.I.
The principal sources of fugitive dust in this area are the new
highway construction and the dust from agricultural tilling and wind
erosion of the newly tilled land. The highway construction dust occurs
year-round whereas the emissions from agriculture are highly seasonal,
occurring in the spring. None of the roads in this area are curbed.
TABLE F.I FUGITIVE DUST EMISSIONS, TONS PER YEAR
Segment
1
2
3
4
5
6
7
8
9
Paved
Roads
1.12
0.79
0.21
0.24
-
1.50
0.77
0.50
_
Unpaved
Roads
7.92
12.90
56.45
Railroads
0.02
0.01
0.01
0.02
0.02
Construction
30.36
30.36
109.08
109.20
Agriculture
1.81
1.90
1.90
2.59
1.90
6.51
8.70
10.31
7.60
Wind
Erosion
23.94
25.08
25.08
34.20
25.08
85.88
114.76
136.04
100.32
103
-------
FIGURE F.I QUARTER MILE AREA SURROUNDING STATION 115
104
-------
FIGURE F.2 STATION 115
DIRECTION - NORTH
105
-------
FIGURE F.3 STATION 115
DIRECTION - NORTH
106
-------
FIGURE F.4 STATION 115
DIRECTION - NE
107
-------
FIGURE F.5 STATION 115
DIRECTION - WEST
108
-------
FIGURE F.6 STATION 115
DIRECTION - SOUTH
109
-------
FIGURE F.7 STATION 115
SURROUNDING AREA TO ONE MILE
1. Approximate Location of New Highway Construction
2. Diversion Channel
110
-------
F.2 FUGITIVE DUST EMISSION CALCULATIONS
SEGMENT 1:
Paved Roads:
Road
Poag Road
Poag Road
Highway 19
Highway 19
Total
Railroads:
ADT
525
1200
950
250
Agricultural Tilling:
% Silt
45
Wind Erosion, Tilled Land:
SEGMENT 2:
Paved Roads:
Road
Poag Road
Highway 19
Total
Active Construction:
ADT
900
950
Time (month)
12
Length (miles)
0.30
0.19
0.25
0.21
Area (acres)
1.84
Area (acres)
63
Area (acres)
63
Length (miles)
0.27
0.25
Area (acres)
2.53
Emissions (tpy)
0.26
0.38
0.39
0.09
1.12
Emissions (tpy)
0.02
Emissions (tpy)
1.81
Emissions (tpy)
23.94
Emissions (tpy)
0.40
0.39
0.79
Emissions (tpy)
30.36
111
-------
Railroads:
Agricultural Tilling:
% Silt
45
Wind Erosion, Tillegl Land:
SEGMENT 3:
Paved Roads:
Road
Highway 19
Rural Road
Total
Agricultural Tilling:
ADT
250
200
% Silt
45
Wind Erosion, Tilled Land:
SEGMENT 4:
Paved Roads:
Road
Poag Road
Railroads:
ADT
550
Area (acres) Emissions (tpy)
1.29 0.01
Area (acres)
66
Area (acres)
66
Length (miles)
0.36
0.17
Area (acres)
66
Area (acres)
66
Length (miles)
0.27
Area (acres)
1.29
Emissions (tpy)
1.90
Emissions (tpy)
25.08
Emissions (tpy)
0.15
0.06
0.21
Emissions (tpy)
1.90
Emissions (tpy)
25.08
Emissions (tpy)
0.24
Emissions (tpy)
0.01
112
-------
Agricultural Tilling:
% Silt Area (acres) Emissions (tpy)
45 90 2.59
Wind Erosion, Tilled Land:
SEGMENT 5:
Active Construction:
Agricultural Tilling:
Time (month)
12
% Silt
45
Wind Erosion, Tilled Land:
SEGMENT 6:
Paved Roads:
Road
Poag Road
Highway 19
Total
ADT
900
950
Area (acres) Emissions (tpy)
90 34.2
Area (acres)
2.53
Area (acres)
66
Area (acres)
66
Length (miles)
0.49
0.49
Unpaved Roads: (gravel)
ADT Length (miles) Speed (mph) % Silt
25 0.59 20 16
Railroads:
Active Construction:
Area (acres)
2.48
Time (month) Area (acres)
12 9.09
Emissions (tpy)
30.36
Emissions (tpy)
1.90
Emissions (tpy)
25.08
Emissions (tpy)
0.73
0.77
1.50
Emissions (tpy)
7.92
Emissions (tpy)
0.02
Emissions (tpy)
109.08
113
-------
Agricultural Tilling:
% Silt
45
Wind Erosion, Tilled. Land:
SEGMENT 7:
Paved Roads:
Road
Highway 19
Agricultural Tilling:
Wind Erosion, Tilled Land:
ADT
650
Silt
45
SEGMENT 8:
Paved Roads:
Area (acres)
226
Area (acres)
226
Length (miles)
0.72
Area (acres)
302
Area (acres)
302
ADT Length (miles)
600 0.51
Road
Poag Road
Unpaved Roads: (gravel)
ADT Length (miles) Speed (mph) % Silt
75 0.32 20 16
Railroads:
Agricultural Tilling:
Area (acres)
2.48
% Silt Area (acres)
45 358
Emissions (tpy)
6.51
Emissions (tpy)
85.88
Emissions (tpy)
0.77
Emissions (tpy)
8.70
Emissions (tpy)
114.76
Emissions (tpy)
0.50
Emissions (tpy)
12.90
Emissions (tpy)
0.02
Emissions (tpy)
10.31
114
-------
Wind Erosion, Tilled Land:
Area (acres) Emissions (tpy)
358 136.04
SEGMENT 9:
Unpaved Roads: (gravel)
ADT Length (miles Speed (mph) % Silt
100 1.05 20 16
Active Construction:
Agricultural Tilling:
Time (month) Area (acres)
12 9.1
% Silt Area (acres)
45 264
Wind Erosion, Tilled Land:
Area (acres)
264
Emissions (tpy)
56.45
Emissions (tpy)
109.20
Emissions (tpy)
7.60
Emissions (tpy)
100.32
115
-------
APPENDIX G
SITE SURVEY - STATION 118
116
-------
CONTENTS
G.I Site Survey - Station 118
6.1.1 Emissions
G.2 Fugitive Dust Emission Calculations
118
120
129
FIGURES
Number
G.I Quarter Mile Area Surrounding Station 118
G.2 Station 118 - Direction-North
G.3 Station 118 - Direction-East
G.4 Station 118 - Direction-SSW
G.5 Station 118 - Direction-West
G.6 Station 118 - Direction-WNW
G.7 Station 118 - Surrounding Area to One Mile
Page
122
123
124
125
126
127
128
TABLES
Number
G.I Fugitive Dust Emissions, Tons Per Year
Page
121
117
-------
G.I SITE SURVEY - STATION 118
Station 118 is located on the Diehl farm in St. Clair County, Illinois.
The site is on the south side of Mule Road approximately 800 ft. east of
Illinois State Highway No. 3. From Highway 3, Mule Road rises to an
elevation of approximately 25 or 30 feet above the level of the highway.
The site is approximately 20 feet south of Mule Road with a narrow driveway
leading to the front of the shelter.
The immediate quarter mile area surrounding the site is shown in Figure
G.I. The land directly north of the site and located between the site and
Mule Road has been tilled and planted right up to the edge of the fence
surrounding the site. Across Mule Road and to the north is a large field
in which corn has been raised throughout the time that the site was in
operation. Immediately east of the site is a plot of land used for a
variety of garden type plants. Approximately 275 ft. to the east and
across the cultivated plot of land is located the nearest building. The
building is a one story farmhouse with the usual type of supporting struc-
tures. East of the farmhouse and across a stretch of cultivated land is
another farmhouse. To the south of the site wheat is the predominant crop.
On the west side of the site and up to the edge of the fence, garden type
plants have been raised. Approximately 400 feet to the west and on the
edge of the tilled land is located another house with wooded areas in the
rear. To the northwest and approximately 400 feet away a seldom used barn
is located on a vegetated strip of land and behind it is a wooded area.
Approximately 500 feet of Federal Aid Secondary Highway 838 is in the
northwest section.
The principal sources of fugitive dust in segment 1 would appear to be
Illinois State Highway No. 3, Mule Road and the agricultural operations
surrounding the site. Highway No. 3 carries an average of 10,700 vehicles
per day. Mule Road averages 125 vehicles per day. Federal Aid Secondary
Highway 838 averages 700 vehicles per day.
118
-------
Segment 2:
A portion of Illinois State Highway 3 runs through the upper right-hand
section of segment 2. This portion of the highway has residential buildings
located on both sides. Along the outer perimeter of the segment the Missouri
Pacific Railroad has a very seldom used roadbed. The tracks are now used
primarily as a siding for storage of rail cars and can be neglected as a
source of fugitive dust. The upper central portion of the segment contains
a small amount of cultivated land but is mostly vegetated and woodland.
Most of the remaining area consists of cultivated farmland. Mule Road runs
through the lower section of the segment. Figures G.2 and G.3 provide a
general view of segment 2.
Segment 3:
This segment is almost wholly cultivated farmland. A small wooded
area occupies the upper central outside perimeter. A small lake is located
in the lower section of the segment. The principal source of fugitive dust
in this segment comes from agricultural activities. Figures G.3 and G.4 are
views of area consisting of segment 3.
Segment 4:
Segment 4 is mainly cultivated farmland. A section of vegetated and
woodland is located in the lower right-hand section; also included in this
area are a few residential houses. Highway 3 passes through the central
part of segment 4. A drainage ditch passes through the upper left-hand
portion of the sector. Figures G.4 and G.5 are views of segment 4.
Segment 5:
Segment 5 is cultivated farmland except for the upper right-hand portion
along the route of Highway 3. Several residences are located along Highway
3. Federal Aid Secondary Highway 838 runs through the central section of
this segment. Figure G.6 is a view of this segment.
Segment 6:
Approximately half of segment 6 is composed of hilly woodland and
119
-------
vegetated land. Illinois Highway 3 traverses the upper left-hand section of
this segment. The lower left-hand section is the residential area of Sugar
Loaf Heights. About 800 feet of the seldom used Missouri Pacific railway
passes through the lower left-hand corner. The entire central section of
this segment is composed of hilly woodland and vegetated land. The culti-
vated areas of this segment are located in the extreme left-hand section and
the lower right corner. A small section of Mule Road passes through this
segment.
Segment 7:
Segment is approximately 1/3 cultivated farmland with the other 2/3 of
the segment being composed of woodlands, a golf course and portions of Diehl
Lake.
Segment 8:
Cultivated farmland comprises approximately 95% of the area of segment
8. One lake and portions of another lake are located in the lower right-hand
corner of the segment. Illinois Highway 3 passes through this portion of the
section. Several small paved roads are located in this segment; traffic maps
indicate an annual average 24 hour traffic volume of less than 75 per day.
On the west side of Illinois Highway 3 there is a small unpaved parking lot
for a discount store. A portion of the drainage ditch from segment 4
extends into this segment in the upper right-hand section.
Segment 9:
Almost the entire area of segment 9 is made up of cultivated farmland.
A portion of the seldom used Missouri Pacific Railroad passes through this
segment. Federal Aid Secondary Highway No. 838 passes through the upper
central portion of this segment and joining Highway 838 at the edge of the
outer perimeter is Federal Aid Highway No. 38.
6.1.1 EMISSIONS
The chief sources of fugitive dust for station 118 are agriculture
and vehicular traffic. Illinois Highway 3 is normally plowed during
snowstorms.
120
-------
Calculations of the fiarticulate emissions are included in section G.2
Lmissions by segments are shown in Table G.I
TABLE G.I FUGITIVE DUST EMISSIONS, TONS PER YEAR
Segment
1
2
3
4
5
6
7
8
9
Paved Roads
6.87
3.41
5.12
2.25
8.86
9.35
0.37
Agricultural
Tilling
3.92
1.96
3.65
3.46
2.97
3.36
5.22
14.89
15.37
Wind Erosion
Tilled Land
35.80
17.90
33.36
31.62
27.09
30.70
47.76
136.08
140.41
121
-------
N
Cultivated
Farmland
FIGURE G.I QUARTER MILE AREA SURROUNDING STATION 118
122
-------
FIGURE G.2 STATION 118
DIRECTION - NORTH
123
-------
FIGURE G.3 STATION 118
DIRECTION - EAST
124
-------
FIGURE G.4 STATION 118
DIRECTION - SSW
125
-------
FIGURE G.5 STATION 118
DIRECTION - WEST
126
-------
FIGURE G.6 STATION 118
DIRECTION - WNW
127
-------
FIGURE G.7 STATION 118
SURROUNDING AREA TO ONE MILE
128
-------
G.2 FUGITIVE DUST EMISSION CALCULATIONS
SEGMENT 1:
Paved Roads:
Road ADT
Illinois State
Highway No. 3 10700
Mule Road 125
Federal Aid Secondary
Highway 838 700
Total
Agricultural Tilling:
% Silt
65
Wind Erosion, Tilled Land:
SEGMENT 2:
Paved Roads:
Road
Illinois State
Highway No. 3
Mule Road
Total
Agricultural Tilling:
ADT
10700
125
Silt
65
Length (miles) Emissions (tpy)
0.38
0.39
0.07
Area (acres)
94.3
Area (acres)
94.3
0.19
0.30
Area (acres)
47.1
6.71
0.08
0.08
6.87
Emissions (tpy)
3.92
Emissions (tpy)
35.8
Length (miles) Emissions (tpy)
3.35
0.06
3.41
Emissions (tpy)
1.96
129
-------
Hind Erosion, Tilled Land:
SEGMENT 3:
Agricultural Tilling:
% Silt
65
Wind Erosion, Tilled Land:
SEGMENT 4:
Paved Roads:
Road
Illinois 3
Agricultural Tilling:
ADT
10700
% Silt
65
Wind Erosion, Tilled Land:
SEGMENT 5:
Paved Roads:
Road
Illinois State
Highway 3
Federal Aid Secondary
Highway 838
Total
Agricultural Tilling:
ADT
10700
700
% Silt
65
Area (acres) Emissions (tpy)
47.1 17.90
Area (acres)
87.8
Area (acres)
87.8
Length (miles)
0.29
Area (acres)
83.2
0.11
0.27
Emissions (tpy)
3.65
Emissions (tpy)
33.36
Emissions (tpy)
5.12
Emissions (tpy)
3.46
Area (acres) Emissions (tpy)
83.2 31.62
Length (miles) Emissions (tpy)
1.94
0.31
2.25
Area (acres) Emissions (tpy)
71.3 2.97
130
-------
Wind Erosion, Tilled Land:
SEGMENT 6:
Paved Roads:
Road
Illinois State
Highway 3
Mule Road
Total
Agricultural Tilling:
ADT
10700
125
% Silt
65
Wind Erosion, Tilled Land:
SEGMENT 7:
Agricultural Tilling:
% Silt
65
Wind Erosion, Tilled Land:
SEGMENT 8:
Paved Roads:
Road
Illinois State
Highw 3
Agricultural Tilling:
ADT
10700
% Silt
65
Area (acres) Emissions (tpy)
71.3 27.09
Length (miles) Emissions (tpy)
0.50
0.17
Area (acres)
80.8
Area (acres)
80.8
Area (acres)
125.7
Area (acres)
125.7
0.53
8.83
0.03
8.86
Emissions (tpy)
3.36
Emissions (tpy)
30.70
Emissions (tpy)
5.22
Emissions (tpy)
47.76
Length (miles) Emissions (tpy)
9.35
Area (acres) Emissions (tpy)
358.1 14.89
131
-------
Wind Erosion, Tilled Land:
SEGMENT 9:
Paved Roads:
Road
ADT
Federal Aid Secondary
Highway 838 450
Agricultural Tilling:
% Silt
65
Wind Erosion, Tilled Land:
Area (acres) Emissions (tpy)
358.1 136.08
Length (miles) Emissions (tpy)
0.5
Area (acres)
369.5
Area (acres)
369.5
0.37
Emissions (tpy)
15.37
Emissions (tpy)
140.41
132
-------
APPENDIX H
SITE SURVEY - STATION 120
133
-------
CONTENTS
H.I Site Survey - Station 120 135
H.I.I Emissions 137
H.2 Fugitive Dust Emission Calculations 146
FIGURES
Number Page
H.I Quarter Mile Area Surrounding Station 120 139
H.2 Station 120 - Direction-WNW 140
H.3 Station 120 - Direction-NE 141
H.4 Station 120 - Direction-NNW 142
H.5 Station 120 - Direction-SE 143
H.6 Station 120 - Direction-SW 144
H.7 Station 120 - Surrounding Area to One Mile 145
TABLES
Number Page
H.I Fugitive Dust Emissions, Tons Per Year 138
134
-------
H.I SITE SURVEY - STATION 120
Station 120 is situated in St. Louis County approximately 14.5 miles
west of downtown St. Louis. The site is located in an area of light com-
mercial business. The immediate quarter mile area is shown in Figure H.I.
There are no significant obstructions near the station. The nearest build-
ing is approximately 125 feet away and is roughly 25 feet tall. The station
is located on the edge of a parking lot for a nearby firm.
In the immediate quarter mile area there is a commercial park to the
west composed of offices, warehouses and repair facilities, as shown in
Figure H.2. To the northeast there is a machining business. To the east and
south there are only vegetated fields. The nearest road is Lackland Road,
700 feet to the north, running east-west. The principal source of fugitive
dust occurred during the construction of the commercial business park,
which largely occurred during 1975 and 1976. Lackland Road carries approxi-
mately 1800 cars per day and constitutes another source of fugitive dust.
The surrounding area to a distance of one mile has been studied. To
the north of the station, approximately 1750 feet, is Page Boulevard running
east-west and carrying 28800 cars per day. This is the principal source of
fugitive dust in sectors 2, 5 and 6. Interstate 270 is located approxi-
mately nine tenths of a mile to the west of the station, running north-south.
This is the largest highway nearby and is in sections 8 and 9. The traffic
on this highway is 93840 cars per day. The intersection of Page Boulevard
and 1-270 is seen in the background of the photograph in Figure H.2.
Segment 2;
Segment 2 is composed of commercial offices, warehouse, light industry
and highways. In addition to Page Boulevard, Schuetz Road intersects Page,.
running north-south, and carries 10050 cars per day. To the NNE of the site,
at approximately 1600 feet, a new commercial office area was constructed
135
-------
during the study period. The construction site was graded before 1975 but,
according to permit dates, the final grading and building site preparation
was done in March 1976. This construction site can be seen in the photo-
graph in Figure H.3, which was taken in the fall of 1975. The site borders
along the southern edge of Page Boulevard. The completed building is seen
in center, right edge of the photograph in Figure H.4. North of the station
in segments 2 and 5, at approximately a half mile, some construction was
performed during the summer of 1976.
Segments 2 and 3:
As shown in Figures H.5 and H.6, segments 3 and 4 are composed of
housing subdivisions and vegetated undeveloped fields. Segment 4 has a
small segment of a road intersecting it running north-south which carries
approximately 10000 cars per day.
Segment 5:
Segment 5 has had some construction, previously mentioned, and has
significant highway traffic on Page Boulevard, Craig Road, and Lackland Road.
Segment 6:
Segment 6 is principally composed of a commercial/industrial park and
Page Boulevard. To the NE at approximately one mile from station 120 is a
concrete pipe manufacturer which may constitute a source of fugitive dust.
Segments 7 and 8:
Segments 7 and 8 are principally residential areas with the exception
of a portion of segment 8 which contains Interstate 270.
Segment 9:
Segment 9 contains the largest portion of West Port Industrial Complex.
In addition the cloverleaf intersection of Interstate 270 and Page Boulevard
is located in this segment.
Beyond the one mile radius surrounding the site there are a few
sources which may have an effect on the fugitive dust reaching the station.
136
-------
To the north approximately 5800 feet there is a concrete supplier. To the
northeast approximately 5800 feet there is a brick manufacturer and just
beyond this is a sanitary landfill for the county.
H.I.I EMISSIONS
The particulate emissions from sources surrounding station 120 have been
calculated and the calculations are included in Section H.2. By far the
largest sources are the highways to the north and west of the station. The
emissions are summarized in Table H.I.
The paved road emissions are present year round. The construction
immediately to the west of the station probably had the greatest influence
on the particulate loading during periods of construction and excavation.
Information on the exact dates of construction are unavailable. Each
construction site is estimated to be one acre and the heavy construction
and grading is estimated to have taken one month. Referring to Figure H.I;
buildings 12 and 16 were under construction in August/September 1975. No
information was available on the dates for buildings 1, 7, 14 and 17.
Buildings 14 and 17 are presently under construction; the grading was
done at the end of 1976. This entire construction site was originally
graded to remove vegetation and partially level the area prior to the study
dates of 1975 and 1976. The construction site was considered as a partic-
ulate source from cleared land for the two year period.
The other major construction area is north of the station in segment 2
along Page Boulevard. This area was graded in March 1976.
137
-------
TABLE H.I FUGITIVE DUST EMISSIONS, TONS PER YEAR
Segment Paved Roads Active Construction Cleared Land
1 2.20 3.0 0.22
2 27.53 6.4 (3/76) 0.07
3 4.78
4 3.44
5 25.47 3.4 (Sum.'76)
6 41.66
7 9.59
8 107.89
9 152.47
138
-------
f Conaressional DP-
2
3
5
7
8
16
rt-
12
10
Borman Dr.
cl
O
0)
to
c.
3
O
o
c
0
o
II
Commtrcioi1
a
Ferguson
machine
P&rkina
FIGURE H.I QUARTER MILE AREA SURROUNDING STATION 120
139
-------
FIGURE H.2 STATION 120
DIRECTION - WNW
140
-------
FIGURE H.3 STATION 120
DIRECTION - NE
141
-------
FIGURE H.4 STATION 120
DIRECTION - NNW
142
-------
FIGURE H.5 STATION 120
DIRECTION - SE
143
-------
FIGURE H.6 STATION 120
DIRECTION - SW
144
-------
FIGURE H.7 STATION 120
SURROUNDING AREA TO ONE MILE
1. Pageview Commerce Center
2. Farm
3, 4. C.V. Mosby Bldg. Const.
5. Watlow Parking Lot Const.
6-13. West Plains Industrial Park
14. Cleared for Building, Fall '76
15. Cleared for Building, Fall '76
16, 17. Cleared for Building, Fall
18. Ortho-Chevron Fertilizer Plant
19. Concrete Pipe Manufacturer
20. Alton Brick
21. St. Louis County Landfill
'76
145
-------
H.2 FUGITIVE DUST EMISSION CALCULATIONS
SEGMENT 1:
Paved Roads:
Road
Lackland
Concourse
Congressional
Ferguson Driveway
Total
*Dirty Street
Cleared Area:
ADT
1800
200
200
300
Length (miles)
0.45
0.30
0.30
0.15
Emissions (tpy)
1.33
0.40*
0.40*
0.07
2.20
Active Construction:
Time (month)
12
SEGMENT 2:
Paved Roads:
Road
Page
Schuetz
Lackland
Total
Cleared Area:
ADT
28800
10050
1800
Area (acres)
20
Area (acres)
3
Length (miles)
0.42
0.44
0.095
Area (acres)
6.4
Emissions (tpy)
0.22
Emissions (tpy)
3.0
Emissions (tpy)
19.95
7.29
0.28
27.52
Emissions (tpy)
0.07
146
-------
Active Construction: (March - April, 1976)
SEGMENT 3:
Paved Roads:
Road
Schuetz
Residential
Total
SEGMENT 4:
Paved Roads:
Road
Craig
Residential
Total
SEGMENT 5:
Paved Roads:
Road
Page
Craig
Lackland
Total
Active Construction:
Time (month)
1
ADT
10050
250
ADT
10000
250
ADT
28800
10000
1800
Area (acres)
6.4
Length (miles)
0.27
0.76
Length (miles)
0.19
0.76
Length (miles)
0.44
0.25
0.15
Emissions (tpy)
6.4
Emissions (tpy)
4.47
0.31
4.78
Emissions (tpy)
3.13
0.31
3.44
Emissions (tpy)
20.91
4.12
0.44
25.47
Time (month)
1
Area (acres)
3.4
Emissions (tpy)
3.4
147
-------
SEGMENT 6:
Paved Roads:
Road
Page
Schuetz
Adie
Lackland
Total
SEGMENT 7:
Paved Roads:
Road
Schuetz
Residential
Total
SEGMENT 8:
Paved Roads:
Road
Craig
1-270
Residential
Total
SEGMENT 9:
Paved Roads:
Road
1-270
Page
West Port
Fee Fee
Marine
Total
ADT
28800
10920
4000
500
ADT
10050
1000
ADT
9530
93840
500
ADT
84680
36570
29729
19000
7690
Length (miles)
0.57
0.57
0.61
0.34
Length (miles)
0.53
0.49
Length (miles)
0.83
0.61
0.47
Length (miles)
0.57
0.57
0.21
0.76
0.34
Emissions (tpy)
27.08
10.27
4.02
0.28
41.65
Emissions (tpy)
8.78
0.81
9.59
Emissions (tpy)
13.05
94.45
0.39
107.89
Emissions (tpy)
79.64
34.39
10.30
23.83
4.31
152.47
148
-------
APPENDIX I
SITE SURVEY - STATION 122
149
-------
CONTENTS
I.I Site Survey - Station 122
1.1.1 Emissions
)
1.2 Fugitive Dust Emission Calculations
151
152
160
FIGURES
Number
I.I Quarter Mile Area Surrounding Station 122
1.2 Station 122 - Direction-West
1.3 One Mile Area Surrounding Station 122
1.4 Station 122 - Direction-SE
1.5 Station 122 - Direction-SW
1.6 Station 122 - Direction-NE
1.7 Station 122 - Direction-South
Page
153
154
155
156
157
158
159
TABLES
Number
I.I Fugitive Dust Emissions, Tons Per Year
Page
152
150
-------
I.I SITE SURVEY - STATION 122
Station 122 is located in Jersey County, Illinois approximately 31 miles
from downtown St. Louis and approximately 13 miles north of Alton, Illinois.
This location is completely surrounded by farmland. The station is on a
slight rise and the nearest objects are some trees to the southwest at
approximately 60 feet.
The immediate quarter mile area surrounding station 122 is shown in
Figure I.I and in the photograph in Figure 1.2. A high level aerial photo-
graph of this area is not available, thus the description of the annular
ring segments will follow the drawing in Figure 1.3.
The station sits on a slight rise with the ground falling away on three
sides into two draws running to the west, filled with trees and shrubs. The
entrance to station 122 is off County Highway 4. As shown in Figure I.I,
the area immediately to the west and north of station 122 is pasture land.
To the southwest of the station and on the east side of Highway 4 are
agricultural farms. The crops in this area are rotated with corn, soybeans
and wheat.
Segments 2 through 5:
Segments 2 and 3, shown in Figure 1.4, are composed entirely of tilled
farmland and short stretches of Highway 4 and the rural road. Segment 4,
shown in Figure 1.5, and segment 5 are approximately two thirds cropland and
one third vegetated pasture.
Segments 6 through 9:
Segment 6 has short stretches of Highway 4 and the rural road. The
rest of the area is entirely cropland, as seen in the background of Figure
1.6. Segment 7, shown in the background of Figure 1.7, is approximately
half cropland and half wooded. Segment 8 is approximately half cropland
151
-------
and half pasture and woods. Segment 9 is partially in pasture and the rest is
cropland.
County Highway 4 carries approximately 125 cars per day and the rural
road carries approximately 50 cars per day.
1.1.1 EMISSIONS
The fugitive dust emissions from the area surrounding station 122 have
been calculated and a summary is presented in Table I.I. The calculations
are included in Section 1.2.
The only significant emissions in this area are from agricultural
tilling and wind erosion of the tilled fields. These emissions are highly
seasonal with most of the emissions occurring in the early spring.
During the summer of 1976 a short section, approximately 200 feet, of
County Highway 4 was under repair which caused extremely dusty conditions.
This section of road is located in segment 3. The rest of this road and the
rural road, which intersects it just north of the station, are paved and in
good condition. None of the roads in this area are curbed.
TABLE I.I FUGITIVE DUST EMISSIONS, TONS PER YEAR
Segment
1
2
3
4
5
6
7
8
9
Paved Roads
0.06
0.07
0.05
-
0.02
0.09
0.10
-
0.05
Agricultural
Tilling
3.94
3.80
3.98
2.82
2.82
16.03
8.47
8.47
16.04
Wind Erosion
- Tilled Land
33.44
32.30
33.82
23.94
23.94
136.04
71.82
71.82
136.04
152
-------
.s
/ Rural ftoqd
Pasture and
Trees
FIGURE I.I QUARTER MILE AREA SURROUNDING STATION 122
153
-------
FIGURE 1.2 STATION 122
DIRECTION - WEST
154
-------
N
Pas-tore
and
Trees
FIGURE 1.3 ONE MILE AREA SURROUNDING STATION 122
155
-------
FIGURE 1.4 STATION 122
DIRECTION - SE
156
-------
FIGURE 1.5 STATION 122
DIRECTION - SW
157
-------
FIGURE 1.6 STATION 122
DIRECTION - NE
158
-------
-
FIGURE 1.7 STATION 122
DIRECTION - SOUTH
159
-------
1.2 FUGITIVE DUST EMISSION CALCULATIONS
SEGMENT 1:
Paved Roads:
Road
County Highway 4
Rural Road
Total
Agricultural Tilling:
ADT
125
50
% Silt
70
Hind Erosion, Tilled Land:
SEGMENT 2:
Paved Roads:
Road
Highway 4
Rural Road
Total
Agricultural Tilling:
ADT
125
50
% Silt
70
Wind Erosion, Tilled Land:
Length (miles)
0.25
0.17
Area (acres)
88
Area (acres)
88
Length (miles)
0.25
0.3
Area (acres)
85
Area (acres)
85
Emissions (tpy)
0.05
0.01
0.06
Emissions (tpy)
3.94
Emissions (tpy)
33.44
Emissions (tpy)
0.05
0.02
0.07
Emissions (tpy)
3.80
Emissions (tpy)
32.30
160
-------
SEGMENT 3:
Paved Roads:
Road
Highway 4
Agricultural Tilling:
ADT
125
% Silt
70
Wind Erosion, Tilled Land:
SEGMENT 4:
Agricultural Tilling:
% Silt
70
Hind Erosion, Tilled Land:
SEGMENT 5:
Paved Roads:
Road
Rural Road
Agricultural Tilling:
ADT
50
% Silt
70
Wind Erosion. Tilled Land:
Length (miles)
0.25
Area (acres)
89
Area (acres)
63
Area (acres)
63
Area (acres)
63
Area (acres)
63
Emissions (tpy)
0.05
Emissions (tpy)
3.98
Area (acres) Emissions (tpy)
89 33.82
Emissions (tpy)
2.82
Emissions (tpy)
23.94
Length (miles) Emissions (tpy)
0.28 0.02
Emissions (tpy)
2.82
Emissions (tpy)
23.94
161
-------
SEGMENT 6:
Paved Roads:
Road
Highway 4
Rural Road
Total
Agricultural Tilling:
ADT
125
50
% Silt
70
Wind Erosion, Tilled Land:
SEGMENT 7:
Paved Roads:
Road
Highway 4
Agricultural Tilling:
ADT
125
% Silt
70
Wind Erosion. Tilled Land:
SEGMENT 8:
Agn'cultural Ti 11 ing:
% Silt
70
Wind Erosion, Tilled Land:
Length (miles)
0.25
0.5
Area (acres)
358
Area (acres)
358
Area (acres)
189
Area (acres)
189
Area (acres)
189
Area (acres)
189
Emissions (tpy)
0.05
0.04
0.09
Emissions (tpy)
16.03
Emissions (tpy)
136.04
Length (miles) Emissions (tpy)
0.5 0.10
Emissions (tpy)
8.47
Emissions (tpy)
71.82
Emissions (tpy)
8.47
Emissions (tpy)
71.82
162
-------
SEGMENT 9:
Paved Roads:
Road
Rural Road
Agricultural Tilling:
ADT
50
% Silt
70
Wind Erosion, Tilled Land:
Length (miles) Emissions (tpy)
0.55 0.05
Area (acres)
358
Area (acres)
358
Emissions (tpy)
16.04
Emissions (tpy)
136.04
163
-------
APPENDIX J
SITE SURVEY - STATION 124
164
-------
CONTENTS
J.I Site Survey - Station 124
J.I.I Emissions
J.2 Fugitive Dust Emission Calculations
166
168
176
FIGURES
Number
J.I Quarter Mile Area Surrounding Station 124
J.2 Station 124 - Direction-East
J.3 Station 124 - Direction-SE
J.4 Station 124 - Direction-SW
J.5 Station 124 - Direction-NW
J.6 Station 124 - Direction-West
J.7 Station 124 - Surrounding Area to One Mile
Page
169
170
171
172
173
174
175
Number
TABLES
J.I Fugitive Dust Emissions, Tons Per Year
Page
168
165
-------
J.I SITE SURVEY - STATION 124
Station 124 is located on the Noble farm in Monroe County approximately
7 miles south of Waterloo, Illinois. The site is located in an agricultural
region where clover, corn and winter crops are predominant. Figure J.I
depicts the immediate quarter mile area surrounding the station. The
station is located on a slightly elevated piece of ground rising above the
surrounding terrain. There are no obstructions nearby and the nearest
structure to the station is a farmhouse and related farm buildings, approxi-
mately 575 ft. to the north-northwest on the opposite side of County Highway
1.
There are cultivated fields in the immediate quarter mile area surround-
ing the station. The owner of the farmland surrounding the station states
that clover, corn, soybean and winter wheat crops are rotated in the fields
adjacent to the station. The nearest road to the station is County Highway
1, approximately 75 ft. on the west side of the station running north and
south. The driveway to the station is approximately 75 ft. long, unpaved
and covered with gravel. County Highway 1 carries approximately 750
vehicles per day. The principal sources of fugitive particulates would
appear to be the cultivated farmland to the north, east, south and west of
the station and County Highway 1.
At the time the photographs were taken, the station, fence and tower
had been removed. However, evidence of the station is clearly visible, as
the driveway and cleared area for the station remain intact.
Segment 2;
Segment 2 is essentially cultivated farmland. There are four or five
residential houses to the north-northeast with one or two small ponds in the
area. County Highway 1 traverses the segment carrying approximately 750
vehicles per day. One of the residential houses was constructed during
166
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1976. Figure J.2 depicts the area contained in segment 2.
Segment 3:
Segment 3 is composed entirely of cultivated farmland and forest area
with patches of woodland between the fields in the east and southeast parts
of the segment. The southern part of the segment contains portions of build-
ings belonging to a farmhouse, Figure J.3.
Segment 4:
Segment 4 is again almost entirely cultivated farmland. Two patches
of woodland are located in the southwest portion of the segment. County
Highway 1 runs through this segment, Figure J.4.
Segment 5:
Segment 5 is approximately 3/4 cultivated farmland and 1/4 wooded area.
The wooded area divides the cultivated portion into two parts with the
largest cultivated area being closest to the station, roughly due west and
northwest of the station, Figure J.5.
Segment 6:
Segment 6 contains mostly cultivated farmland with patches of woodland
scattered throughout. A small lake is located in the northeast section of
the segment and County Highway 1 runs from north to south with several
farm roads located chiefly in the lower right-hand section. Several resi-
dential houses are located on both sides of County Highway 1.
Segment 7:
Segment 7 is mostly cultivated farmland with scattered areas of woodland.
Segment 8:
Segment 8 is mostly cultivated farmland with County Highway 1 running
through the lower section. A small wooded area is located in the upper
left-hand section.
167
-------
Segment 9:
Segment 9 is also mostly cultivated farmland with a small area of
woodland in the lower, central and right sections of the segment.
County Highway 1 is plowed during snowfalls with no salt or other
melting agents spread on the roadway. The areas outside of the segments
are approximately of the same general makeup as those inside the segments,
that is, mostly cultivated farmland. An overview of the site is illustrated
in Figure J.6.
J.I.I EMISSIONS
Calculations of the particulate emissions are included in Section J.2.
Emissions by segments are shown in Table J.I. The principal sources of
fugitive particulates are emissions from agricultural tilling, wind erosion
from tilled land and County Highway 1.
__. TABLE J.I FUGITIVE DUST EMISSIONS. TONS PER YEAR
Active Agricultural Wind Erosion
Segment Paved Roads Construction Ti11ing - Tilled Land
1 0.62 4.78 43.70
2 0.31 0.25 (1976) 3.74 34.20
3 - 3.58 32.68
4 0.34 3.58 32.68
5 - 3.03 27.74
6 0.65 13.39 122.36
7 - 12.27 112.10
8 0.65 14.80 135.28
9 - 14.30 ' 130.72
168
-------
FIGURE J.I QUARTER MILE AREA SURROUNDING STATION 124
169
-------
FIGURE J.2 STATION 124
DIRECTION -EAST
170
-------
FIGURE J.3 STATION 124
DIRECTION - SE
171
-------
FIGURE J.4 STATION 124
DIRECTION - SW
172
-------
FIGURE J.5 STATION 124
DIRECTION - NW
173
-------
FIGURE J.6 STATION 124
DIRECTION - WEST
174
-------
FIGURE J.7 STATION 124
SURROUNDING AREA TO ONE MILE
175
-------
J.2 FUGITIVE DUST EMISSION CALCULATIONS
SEGMENT 1:
Paved Roads:
Road
County Highway 1
Agricultural Tilling:
ADT
750
% Silt
65
Wind Erosion, Tilled Land:
SEGMENT 2:
Paved Roads:
Road ADT
County Highway 1 750
Active Construction:
Time (month)
1
Agricultural Tilling:
% Silt
65
Wind Erosion, Tilled Land:
Length (miles)
0.5
Area (acres)
115
Area (acres)
115
Length (miles)
0.25
Area (acres)
0.25
Area (acres)
90
Area (acres)
90
Emissions (tpy)
0.62
Emissions (tpy)
4.78
Emissions (tpy)
43.7
Emissions (tpy)
0.31
Emissions (tpy)
0.25
Emissions (tpy)
3.74
Emissions (tpy)
34.2
176
-------
SEGMENT 3:
Agricultural Tilling:
% Silt
65
Wind Erosion, Tilled Land:
SEGMENT 4:
Paved Roads:
Road
County Highway 1
Agricultural Tilling:
ADT
750
% Silt
65
Wind Erosion, Tilled Land:
SEGMENT 5:
Agricultural Tilling:
% Silt
65
Wind Erosion, Tilled Land:
SEGMENT 6:
Paved Roads:
Road
County Highway 1
ADT
750
Area (acres)
86
Area (acres)
86
Area (acres)
86
Area (acres)
86
Area (acres)
73
Area (acres)
73
Emissions (tpy)
3.58
Emissions (tpy)
32.68
Length (miles) Emissions (tpy)
0.25 0.34
Emissions (tpy)
3.58
Emissions (tpy)
32.68
Emissions (tpy)
3.03
Emissions (tpy)
27.74
Length (miles) Emissions (tpy)
0.53 0.65
177
-------
Agricultural Tilling:
% Silt
65
Wind Erosion, Tilled Land:
SEGMENT 7:
Agricultural Tilling:
% Silt
65
Wind Erosion, Tilled Land:
SEGMENT 8:
Paved Roads:
Road
County Highway 1
Agricultural Tilling:
ADT
750
% Silt
65
Wind Erosion, Tilled Land:
SEGMENT 9:
Agricultural Tilling:
% Silt
65
Wind Erosion, Tilled Land:
Area (acres)
322
Area (acres)
222
Emissions (tpy)
13.39
Emissions (tpy)
122.36
Area (acres)
295
Area (acres)
295
Emissions (tpy)
12.27
Emissions (tpy)
112.10
Length (miles)
0.53
Area (acres)
356
Area (acres)
356
Emissions (tpy)
0.65
Emission (tpy)
14.80
Emissions (tpy)
135.28
Area (acres)
344
Area (acres)
344
Emissions (tpy)
14.30
Emissions (tpy)
130.72
178
-------
APPENDIX K
SITE SURVEY - 14th & MARKET
179
-------
CONTENTS
K.I Site Survey - HI-Vol Site - 14th and Market
K.I.I Emissions
K.2 Fugitive Dust Emission Calculations
181
183
191
FIGURES
Number
K.I Quarter Mile Area Surrounding Hi-Vol Site at
14th and Market Streets
K.2 14th and Market Site - Direction-NW
K.3 14th and Market Site - Direction-West
K.4 14th and Market Site - Direction-North
K.5 14th and Market Site - Direction-East
K.6 14th and Market Site - Direction-South
K.7 14th and Market Site - Surrounding Area to One Mile
Page
184
185
186
187
188
189
190
Number
TABLES
K.I Fugitive Dust Emissions, Tons Per Year
Page
183
180
-------
K.I SITE SURVEY - HI-VOL SITE - 14TH AND MARKET
This site was part of a special study conducted by Dr. William Wilson,
United States Environmental Protection Agency. The Hi-Vol sampler was
located on the roof of the Municipal Courts Building at 14th and Market
Streets in downtown St. Louis. This building is four stories high which
puts the Hi-Vol at least 50 feet above the street.
The immediate quarter mile area is shown in Figure K.I and the photo-
graph in Figure K.2. There are several buildings in the area which are
higher than the sampler location. The closest obstruction is the Kiel
Auditorium which is approximately 150 feet east of the courts building and
is 30-50 feet higher than the courts building, Figures K.3 and K.4. This
area is principally high-rise office buildings and commercial offices.
There are several parking areas which hold approximately 1000 cars during
working hours. With the exception of the heavily trafficked streets, there
are no significant sources of fugitive dust. This is also the case for the
majority of the one mile radius survey area.
Segment 2;
Segment 2 is composed of high-rise office buildings and busy downtown
streets. There are only a few surface parking lots in this area.
Segment 3:
Segment 3 contains half of Busch Stadium, Figure K.5. The stadium is
surrounded by several parking lots which hold approximately 1000 cars and a
stadium garage which holds a couple thousand cars. These lots are used for
daily parking, as well as stadium events. U. S. Highway 40 passes through
this segment. Part of a railroad yard is located in this segment.
181
-------
Segment 4:
Segment 4 is principally railroad yards. The rail entrance to Union
Station is in this segment. Highway 40 passes through this segment as seen
in Figure K.6.
Segment 5:
Segment 5 is composed of high-rise office buildings and busy downtown
streets. The main post office is in this segment and probably attracts
considerable traffic.
Segment 6:
Segment 6 is where most of the recent construction has taken place. The
convention center which occupies 6-8 city blocks has been under construction
for all of 1975 and 1976. The Mercantile Trust building is the.tallest
building in downtown St. Louis and the upper levels were still under con-
struction in 1975. Interstate 70 passes through this segment.
Segment 7:
Segment 7 contains the other half of Busch Stadium. There are several
parking areas in this segment. This segment is the location of the Jefferson
Memorial Park and the Gateway Arch. The intersection of Interstate 70,
Highway 40 and Interstate 55 is in this segment as well as stretches of each.
Some construction has taken place along Interstate 55 during 1976 in an
effort to widen the roadway. A new housing development has been under con-
struction during 1975 and 1976 in this segment. This covers a 6 block area.
A few small trucking firms are located in this segment which handle approxi-
mately 200 trucks per day.
Segment 8:
Segment 8 is approximately half comprised of multi-family residences.
The City Hospital is in this segment. Highway 40 and some rail yards are in
this segment. The rest of the area is covered with commercial businesses.
182
-------
Segment 9:
Segment 9 is approximately two-thirds commercial offices and warehouses
and one-third multi-family residences, in the northern part.
K.I.I EMISSIONS
The calculations of the fugitive dust emissions in the area surrounding
this special Hi-Vol site are included in Section K.2. A summary of the
emissions by segment is shown in Table K.I.
The principal sources of fugitive dust in this area are entrainment
from traffic on paved roads and construction, both of which occur year round.
All streets in this area are curbed. The height of this site and all of the
tall buildings in the downtown area probably greatly diminish the actual
effects of these sources.
TABLE K.I FUGITIVE DUST EMISSIONS, TONS PER YEAR
Segment
1
2
3
4
5
6
7
8
9
Paved Roads
81.69
53.93
61.77
55.19
42.30
155.05
291.63
122.41
102.77
Construction Rail Yards
0.19
0.25
304.8
175.2
0.23
183
-------
FIGURE K.I QUARTER MILE AREA SURROUNDING HI-VOL SITE AT
14TH AND MARKET STREETS
184
-------
FIGURE K.2 14TH AND MARKET SITE
DIRECTION - NW
185
-------
FIGURE K.3 14TH AND MARKET SITE
DIRECTION - WEST
186
-------
FIGURE K.4 14TH AND MARKET SITE
DIRECTION - NORTH
187
-------
J
FIGURE K.5 14TH AND MARKET SITE
DIRECTION - EAST
188
-------
FIGURE K.6 14TH AND MARKET SITE
DIRECTION - SOUTH
189
-------
FIGURE K.7 14TH AND MARKtT SITE
SURROUNDING AREA TO ONE MILE
1. Municipal Courts
2. City Hall
3. Kiel Auditorium
4. Veteran's Administration
5. Federal Bldg. & Post Office
6. Union Station
>
7. Convention Center
8. Mercantile Trust
9. Busch Stadium
10. Gateway Arch
11. New Housing Development
190
-------
K.2 FUGITIVE DUST EMISSION CALCULATIONS
SEGMENT 1:
Paved Roads:
Road
Market St.
14th St.
12th St.
Olive Blvd.
City Streets
Total
SEGMENT 2:
Paved Roads:
Road
Olive Blvd.
Washington Ave.
12th St.
City Streets
Total
SEGMENT 3:
Paved Roads:
Road
Market St.
U.S. 40
City Streets
Total
Railroads:
ADT
20000
11460
14000
10170
10000
ADT
10170
9660
14000
10000
ADT
19000
48700
10000
Length (miles)
0.47
0.47
0.42
0.27
2.61
Length (miles)
0.32
0.44
0.27
2.14
Length (miles)
0.25
0.34
1.61
Emissions (tpy)
15.51
8.89
9.70
4.53
43.06
81.69
Emissions (tpy)
5.37
7.01
6.24
35.31
53.93
Emissions (tpy)
7.84
27.37
26.36
61.57
Area (acres)
20.7
Emissions (tpy)
0.19
191
-------
SEGMENT 4:
Paved Roads:
Road
U.S. 40
14th St.
City Streets
Total
Railroads:
SEGMENT 5:
Paved Roads:
Road
Market St.
Olive Blvd.
Washington Ave.
City Streets
Total
SEGMENT 6:
Paved Roads:
Road
Interstate 70
12th St.
Washington Ave.
Martin Luther King
Bridge
Eads Bridge
Del mar Blvd.
Martin Luther King Dri
Broadway
City Streets
Total
ADT
56150
10970
5000
ADT
20000
13410
9660
10000
ADT
85000
14000
10000
5100
3650
6000
ve 4980
7420
5000
Length (miles)
0.49
0.25
0.64
Area (acres)
27.5
Length (miles)
0.25
0.30
0.25
1.42
Length (miles)
0.61
0.47
0.38
0.13
0.17
0.49
0.49
0.57
4.17
Emissions (tpy)
45.39
4.52
5.28
55.19
Emissions (tpy)
0.25
Emissions (tpy)
8.25
6.63
3.98
23.43
42.29
Emissions (tpy)
85.55
10.86
6.27
1.09
1.02
4.85
4.03
6.98
34.40
155.05
192
-------
Active Construction:
SEGMENT 7:
Paved Roads:
Road
Interstate 70
U.S. 40
Interstate 55
Poplar St. Bridge
7th Street
Broadway
Chouteau Ave.
City Streets
Total
Construction:
SEGMENT 8:
Paved Roads:
Road
U.S. 40
Jefferson Ave.
Chouteau Ave.
14th St.
12th St.
City Streets
Total
Time (month)
12
ADT
81050
48700
85800
91360
5100
7400
7470
7500
Time (month)
12
ADT
56150
17880
10000
10970
16880
5000
Area (acres)
25.4
Length (miles)
0.47
0.42
0.80
0.11
0.64
0.98
0.45
3.41
Area (acres)
14.6
Length (miles)
0.47
0.30
0.95
0.49
0.51
3.79
Emissions (tpy)
304.8
Emissions (tpy)
62.85
33.75
113.26
16.67
5.38
11.96
5.54
42.20
291.61
Emissions (tpy)
175.2
Emissions (tpy)
43.54
8.85
15.67
8.87
14.20
31.26
122.39
Railroads:
Area (acres)
24.8
Emissions (tpy)
0.23
193
-------
SEGMENT 9:
Paved Roads:
Road ADT Length (miles) Emissions (tpy)
Market St. 20000 0.49 16.17
Jefferson Ave. 17720 0.76 22.22
Olive Blvd. 13410 0.51 11.28
Washington AVe. 9800 0.57 9.22
Delmar Blvd. 3720 0.68 4.17
Martin Luther King'
Drive 5980 0.70 6.90
City Streets , 3500 5.68 32.80
Total 102.76
194
-------
APPENDIX L
SITE SURVEY - S. BROADWAY & HURCK
195
-------
CONTENTS
L.I Site Survey - Hi-Vol Site - S. Broadway & Hurck 197
L.I.I Emissions 199
L.2 Fugitive Dust Emission Calculations 208
FIGURES
Number Page
L.I Quarter Mile Area Surrounding Hi-Vol Station
at S. Broadway and Hurck Sts. 201
L.2 S. Broadway & Hurck Site - Direction-NW 202
L.3 S. Broadway & Hurck Site - Direction-NE 203
L.4 S. Broadway & Hurck Site - Direction-East 204
L.5 S. Broadway & Hurck Site - Direction-NW 205
L.6 S. Broadway & Hurck Site - Direction-SW 206
L.7 S. Broadway & Hurck Site - Sourrounding Area to One Mile 207
TABLES
Number Page
L.I Fugitive Dust Emissions, Tons Per Year 200
196
-------
L.I SITE SURVEY - HI-VOL SITE - S. BROADWAY & HURCK
This site was part of a special study conducted by Dr. William Wilson,
United States Environmental Protection Agency. The Hi-Vol sampler was
located on the roof of an old fire station on the northwest corner of
S. Broadway and Hurck streets. This site is also the location for the No. 2
sampling station in the St. Louis City monitoring network. This location is
approximately 6.5 miles southeast of downtown St. Louis.
The immediate quarter mile area is shown in Figure L.I and the photo-
graph in Figure L.2. This area is primarily residential. To the northeast
of the site is the local business district which starts at about a quarter
mile. The nearest obstructions that could affect the Hi-Vol data are the
hose tower and stairway which extend ten feet above the roof of the firehouse
in the northern corner and a large tree northeast of the firehouse which is
at least fifteen feet higher than the roof. These obstructions can be seen
in Figures L.3 and L.4. South Broadway is a fairly busy street and carries
11830 cars per day. The other major street is Marceau which crosses
S. Broadway one block south of Hurck. Marceau carries 5520 cars per day.
Marceau was under construction during 1975 for widening and resurfacing.
Segment 2:
Segment 2 is a mixture of residential and commercial areas. Approxi-
mately 40 percent of the area is residential. S. Broadway in this area is
lined with retail businesses. Between S. Broadway and the Mississippi River
there are small industrial operations. A small foundry operation, Liberty
Foundry, is located a half mile northeast of the Hi-Vol site. This may
contribute particulates collected at the Hi-Vol site, however, there is no
information available on the emissions from this company. During the site
survey there were no significant particulate emissions from the foundry.
197
-------
Segment 3:
Segment 3 is heavily industrialized. Almost a half mile east of the
Hi-Vol site is the Fowles Grain Co. Southeast of the site, along the river,
is the St. Louis Shipyards. In the southern section of this segment is the
main production area of Great Lakes Carbon (RAPS Source 26-4280-12). This
plant produces metallurgical coke, with emissions from its stacks of 40
tons per year.
Segment 4:
Segment 4 is mostly covered by River Des Peres Drainage Channel. There
are some residences in this area and several open, grass-covered areas.
Along S. Broadway there are some commercial companies.
Segment 5:
Segment 5 is approximately half residential. Half of a Monsanto
industrial plant manufacturing phosphate salts for dentifrice and other uses
is located in this segment. At times this operation could have particulate
emissions, however nothing significant was observed during the site survey.
This plant can be seen in background of Figure L.5. There are several
other, smaller industrial companies in this area, none of which have any
significant particulate emissions.
Segment 6:
Segment 6 is approximately half residential. Interstate 55 cuts through
the northern corner of this segment and carries 72150 cars per day. Between
S. Broadway and the Mississippi River are some small industries, storage
yards and river terminals. The river covers almost a quarter of this
segment.
Segment 7:
Segment 7 is more than half covered by the Mississippi River. The
eastern bank is covered with farmland. Part of the coal storage area for
Great Lakes Carbon is in this segment. In the southern tip of this segment
is N. L. Industries (RAPS Source 26-4300-09). This plant manufactures
198
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titanium dioxide pigment and several times has had outages of sulfur dioxide
and sulfuric acid mist. Both of these plants can be seen in the background
of Figure L.6.
Segment 8:
Segment 8 is approximately half residential. The lower half of this
segment contains the Metropolitan Sewer District treatment plant, the
Defense Mapping Agency, part of N. L. Industries and a rail yard. In the
northern section of this segment, along Lemay Ferry Road, is a local
business district.
Segment 9;
Segment 9 is about one third residential. The major source of dust in
this segment would be entrained from traffic on Interstate 55. Part of the
Monsanto plant is in this segment. There are also some commercial and light
industrial operations in this segment, none of which constitute any signifi-
cant particulate sources.
L.I.I EMISSIONS
The calculations of the fugitive dust emissions in the area surrounding
this special Hi-Vol site are included in Section L.2. A summary of the
emissions by segment is shown in Table L.I.
The principal source of fugitive dust in this area is entrainment
from traffic on paved roads. Almost all of the streets in this area are
paved. The other sources of particulates are local industry and the
construction which took place on Marceau Street, just a block away from the
site.
199
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TABLE L.I FUGITIVE DUST EMISSIONS, TONS PER YEAR
Paved Cleared
Segment Roads Land Construction Rail Yards
1
2
3
4
5
6
7
8
9
20.22
1364
4.15
6.23
16.67
60.70
-
28.44
112.02
21.6 (1975)
0.08
0.40
-
0.04
0.33
0.14
0.15 0.13
0.12
Agriculture Wind Erosion
0.27 2.66
2.84 28.10
200
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FIGURE L.I QUARTER MILE AREA SURROUNDING HI-VOL STATION
AT S. BROADWAY AND HURCK STS.
201
-------
FIGURE 1.2 S. BROADWAY & HURCK SITE
DIRECTION - NW
202
-------
-
FIGURE L.3 S. BROADWAY & HURCK SITE
DIRECTION - NE
203
-------
FIGURE L.4 S. BROADWAY & HURCK SITE
DIRECTION - EAST
204
-------
FIGURE L.5 S. BROADWAY & HURCK SITE
DIRECTION - NW
205
-------
FIGURE L.6 S. BROADWAY & HURCK SITE
DIRECTION - SW
206
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FIGURE L.7. S. BROADWAY & HURCK SITE
SURROUNDING AREA TO ONE MILE
1. Marceau Ave. Construction
2. Liberty Foundry
3. Fowles Grain Elevator
4. St. Louis Shipyards
5. Great Lakes Carbon
6. N. L. Industries
7. Metropolitan Sewer District
8. Monsanto
207
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L.2 FUGITIVE DUST EMISSION CALCULATIONS
SEGMENT 1:
Paved Roads:
Road
S. Broadway
Marceau
Residential Sts.
Total
Active Construction:
ADT
11830
5520
1500
Time (month)
12
SEGMENT 2:
Paved Roads:
Road
S. Broadway
Ivory
Residential Sts.
Total
Cleared Areas:
SEGMENT 3:
Paved Roads:
Road
Local Business Sts,
ADT
11830
6000
1500
ADT
1000
Length (miles)
0.49
0.45
2.65
Area (acres)
1.8
Length (miles)
0.25
0.15
2.94
Area (acres)
6.9
Length (miles)
0.63
Emissions (tpy)
9.56
4.10
6.56
20.22
Emissions (tpy)
21.6
Emissions (tpy)
4.88
1.48
7.27
13.63
Emissions (tpy)
0.08
Emissions (tpy)
4.15*
*dirty street
208
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Cleared Areas:
SEGMENT 4:
Paved Roads:
Road
S. Broadway
Residential
Total
SEGMENT 5:
Paved Roads:
Road
Lemay Ferry Rd.
Marceau
Germania
Residential
Total
Cleared Areas:
SEGMENT 6:
Paved Roads:
Road
S. Broadway
Interstate 55
Loughborough Ave.
Michigan Ave.
Residential
Total
Area (acres)
35.8
Emissions (tpy)
0.40
ADT
14830
200
ADT
12000
5520
11900
750
ADT
11700
72150
7500
5330
750
Length (miles)
0.25
0.34
Length (miles)
0.63
0.19
0.09
0.57
Area (acres)
3.4
Length (miles)
0.49
0.30
0.45
0.51
4.43
Emissions (tpy)
6.12
0.11
6.23
Emissions (tpy)
12.47
1.73
1.76
0.70
16.65
Emissions (tpy)
0.04
Emissions (tpy)
9.46
35.71
5.57
4.48
5.48
60.70
209
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Cleared Areas:
Agricultural Tilling:
% Silt
60
Hind Erosion, Tilled Land:
SEGMENT 7:
Cleared Areas:
Agricultural Tilling:
% Silt
60
Wind Erosion, Tilled Land:
SEGMENT 8:
Paved Roads:
Road
S. Broadway
Lemay Ferry Rd.
Residential
Total
Railroads:
ADT
12660
17870
750
Area (acres) Emissions (tpy)
30.3 0.33
Area (acres) Emissions (tpy)
7 0.27
Area (acres) Emissions (tpy)
7 2.66
Area (acres) Emissions (tpy)
12.4 0.14
Area (acres)
74
Area (acres)
74
Length (miles)
0.50
0.47
3.35
Area (acres)
13.8
Emissions (tpy)
2.84
Emissions (tpy)
28.1
Emissions (tpy)
10.44
13.86
4.14
28.44
Emissions (tpy)
0.13
210
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Cleared Areas:
Area (acres)
13.5
SEGMENT 9:
Paved Roads:
Road
Interstate 55
Germania
Carondolet
Residential
Total
Cleared Areas:
ADT Length (miles)
70740 0.76
11900 0.63
6270 0.66
750 3.33
Area (acres)
11
Emissions (tpy)
0.15
Emissions (tpy)
88.70
12.37
6.82
4.12
112.01
Emissions (tpy)
0.12
211
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