U.S. ENVIRONMENTAL PROTECTION AGENCY
NATIONAL EUTROPHICATION SURVEY
WORKING PAPER SERIES
RETORT
ON
SHELBYVILLE RESERVOIR
MDULTRIE AND SHELBY COUNTIES
ILLINOIS
EPA REGION V
WORKING PAPER No, 315
^ORVALLIS ENVIRONMENTAL RESEARCH LABORATORY - CORVALLIS, OREGON
and
ENVIRONMENTAL MONITORING & SUPPORT LABORATORY - LAS VEGAS, NEVADA
699-440
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REPORT
ON
SHELBYVILLE RESERVOIR
AND SHELBY COUNTIES
ILLINOIS
EPA REGION V
WORKING PAPER No, 315
WITH THE COOPERATION OF THE
ILLINOIS ENVIRONMENTAL PROTECTION AGENCY
AND THE
ILLINOIS NATIONAL GUARD
JUNE, 1975
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I
CONTENTS
Page
Foreword jj
List of Illinois Study Lakes Iv
Lake and Drainage Area Map v
Sections
I. Conclusions 1
II. Lake and Drainage Basin Characteristics 4
III. Lake Water Quality Summary 5
IV. Nutrient Loadings 10
V. Literature Reviewed 17
VI. Appendices 18
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ii
FOREWORD
The National Eutrophication Survey was initiated In 1972 in
response to an Administration comitment to investigate the nation-
wide threat of accelerated eutrophication to fresh water lakes and
reservoirs.
OBJECTIVES
The Survey was designed to develop, in conjunction with state
environmental agencies, Information on nutrient sources, concentrations,
and impact on selected freshwater lakes as a basis for formulating
comprehensive and coordinated national, regional, and state management
practices relating to point-source discharge reduction and non-point
source pollution abatement in lake watersheds.
ANALYTIC APPROACH
The mathematical and statistical procedures selected for the
Survey’s eutrophication analysis are based on related concepts that:
a. A generalized representation or model relating
sources, concentrations, and impacts can be constructed.
b. By applying measurements of relevant parameters
associated with lake degradation, the generalized model
can be transformed into an operational representation of
a lake, its drainage basin, and related nutrients.
c. With such a transformation, an assessment of the
potential for eutrophication control can be made.
LAKE ANALYSIS
In this report, the first stage of evaluation of lake and water-
shed data collected from the study lake and its drainage basin is
documented. The report is formatted to provide state environmental
agencies with specific information for basin planning [ 3O3(e)], water
quality criteria/standards review [ 3O3(c)], clean lakes [ 314(a,b)J,
and water quality monitoring [ 1O6 and §305(b)] activities mandated
by the Federal Water Pollution Control Act Amendments of 1972.
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iii
Beyond the single lake analysis, broader based correlations
between nutrient concentrations (and loading) and trophic condi-
tion are being made to advance the rationale and data base for
refinement of nutrient water quality criteria for the Nation’s
fresh water lakes. Likewise, multivariate evaluations for the
relationships between land use, nutrient export, and trophic
condition, by lake class or use, are being developed to assist
in the formulation of planning guidelines and policies by EPA
and to augment plans implementation by the states.
ACKNOWLEDGMENT
The staff of the National Eutrophication Survey (Office of
Research & Development, U. S. Environmental Protection Agency)
expresses sincere appreciation to the Illinois Environmental
Protection Agency for professional involvement and to the
Illinois National Guard for conducting the tributary sampling
phase of the Survey.
Dr. Richard H. Briceland, Director of the Illinois Environ-
mental Protection Agency; and Ronald M. Barganz, State Survey
Coordinator, and John J. Forneris, Manager of Region III, Field
Operations Section of the Division of Water Pollution Control,
provided invaluable lake documentation and counsel during the
Survey, reviewed the preliminary reports, and provided critiques
most useful in the preparation of this Working Paper series.
Major General Harold R. Patton, the Adjutant General of
Illinois, and Project Officer Colonel Daniel L. Fane, who directed
the volunteer efforts of the Illinois National Guardsmen, are also
gratefully acknowledged for their assistance to the Survey.
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iv
NATIONAL EUTROPHICATION SURVEY
STUDY LAKES
STATE OF ILLINOIS
LAKE NAME COUNTY
Baldwin Randolph
Bloomington McLean
Carlyle Bond, Clinton, Fayette
Cedar Lake
Charleston Coles
Coffeen Montgomery
Crab Orchard Jackson, Williamson
Decatur Macon
DePue Bureau
East Loon Lake
Fox Lake
Grass Lake
Highland Silver Madison
Holiday LaSalle
Horseshoe Madison
Long Lake
Lou Yaeger Montgomery
Marie Lake
Old Ben Mine Franklin
Pistakee Lake, McHenry
Raccoon Marion
Rend Franklin, Jefferson
Sangchris Christian
Shelbyville Moultrie, Shelby
Slocum Lake
Springfield Sangamon
Storey Knox
Vandalia Fayette
Vermilion Vermilion
Wee Ma Tuk Fulton
Wonder McHenry
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SHE LBYVILLE
RESERVOIR
Tributary Sampling Site
lake Sampling Site
Sewage Treatment Facility
Drainage Area Boundary
I?
Industrial Water
Supply Co.
coIo
7
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SHELBYVILLE RESERVOIR
STORET NO. 1739
I. CONCLUSIONS
A. Trophic Condition:
Survey data indicate Shelbyville Reservoir is eutrophic.
Of the 31 Illinois water bodies sampled in 1973, Shelbyville
Reservoir ranked tenth in overall trophic quality using a
combination of six water quality parameters*. Five of the
lakes had less median total phosphorus, eight had less median
dissolved phosphorus, 25 had less median inorganic nitrogen,
nine had less mean chlorophyll a, and five had greater mean
Secchi disc transparency. Depression of dissolved oxygen
with depth occurred at all sampling stations in August and at
stations 1 and 2 in October, 1973.
During their visits to the reservoir, Survey limnologists
did not observe any nuisance conditions.
B. Rate-Limiting Nutrient:
The algal assay results indicate Shelbyville Reservoir was
phosphorus limited at the time the sample was collected (05/08/73).
The reservoir data indicate phosphorus limitation at the other
sampling times as well.
* See Appendix A.
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2
C. Nutrient Controllability:
1. Point sources-—The phosphorus contribution of point
sources amounted to 21.0% of the total load reaching the
reservoir during the sampling year. The Urbana-Champaign
Sanitary District plant contributed 12.3% of the total load;
the Sullivan plant, 2.8%; the Authur plant, 1.3%; the nine
other domestic plants collectively contributed 4.6%; and the
U.S. Industrial Water Supply Company contributed 0.7%.
Survey data indicate a total phosphorus loading rate of
4.12 g/m 2 /yr which is nearly six times the rate proposed by
Vollenweider (Vollenweider and Dillon, 1974) as a eutrophic
rate (see page 16). While even 100% phosphorus removal at the
above point sources would only reduce the loading rate to 3.26
g/m 2 /yr (over four times the eutrophic rate), the reservoir is
phosphorus limited, and any substantial reduction in phosphorus
input should result in at least some improvement in the trophic
condition of Shelbyville Reservoir, particularly if significant
portions of the phosphorus export of three of the reservoir
tributaries prove to be controllable (see below).
2. Non-point sources--The phosphorus export rates of the
Kaskaskia River (69 kg/kni 2 /yr), Asa Creek (145 kg/km 2 /yr), and
Marrowbone Creek (95 kg/km 2 /yr) exceeded the rates of the other
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six Shelbyville tributaries (mean of 31 kg/km2/yr, range of
20 to 44 kg/km2/yr; see page 15).
It seems unlikely that the high rates of the three
streams resulted solely from underestimation of the point-
source phosphorus loads; e.g., the Kaskaskia River phos-
phorus load would have to be reduced by over 32,000 kg (36%)
to lower the export rate to 44 kg/km2/yr. Similarly, the
Marrowbone Creek load would have to be reduced 7,800 kg (54%),
and the Asa Creek load would have to be reduced nearly 3,600
kg (70%).
Since all point sources known to the Illinois Environmental
Protection Agency were accounted for, it appears that land-use
practices in the three drainages differ markedly from the
practices in the other Shelbyville tributary drainages. How-
ever, a more-detailed study of the three streams is needed
to confirm this.
The Kaskaskia River accounted for 49.4% of the total phos-
phorus input to the reservoir, and Marrowbone Creek contributed
7.8%. Wilborn Creek and the unnamed creek (B-l) were the
lowest with 0.5% and 0.4%, respectively. The minor tributaries
and immediate drainage were estimated to have contributed 5.0%
of the total phosphorus input to the reservoir.
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4
II. LAKE AND DRAINAGE BASIN CHARACTERISTICSt
A. Lake Morphometrytt:
1. Surface area: 44.52 kilometers 2 .
2. Mean depth: 5.0 meters.
3. Maximum depth: >15.5 meters.
4. Volume: 222.028 x 106 m 3 .
5. Mean hydraulic retention time: 131 days.
B. Tributary and Outlet:
(See Appendix C for flow data)
1. Tributaries -
Drainage Mean flow
Name area (km 2 )* ( m 3 /sec)*
Kaskaskia River 1,310.5 9.3
Unnamed Creek (B-i) 32.9 0.2
Wilborn Creek 43.3 0.3
West Okaw Creek 442.9 2.9
Marrowbone Creek 150.7 1.0
Asa Creek 35.2 0.2
Jonathan Creek 146.9 0.9
Whitley Creek 118.9 0.8
Sand Creek 54.1 0.3
Minor tributaries &
immediate drainage - 350.0 3.7
Totals 2,685.4 19.6
2. Outlet -
Kaskaskia River 2,729.9** 19.6
C. Precipitation***:
1. Year of sampling: 155.7 centimeters.
2. Mean annual : 97.4 centimeters.
t Table of metric conversions--Appendix B.
tt Forneris, 1973.
* For limits of accuracy, see Working Paper No. 175, “...Survey Methods,
1973—1976”.
** Includes area of lake,
See Working Paper No. 175.
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5
III. LAKE WATER QUALITY SUMMARY
Shelbyville Reservoir was sampled three times during the open-water
season of 1973 by means of a pontoon-equipped Huey helicopter. Each
time, samples for physical and chemical parameters were collected from
six stations on the lake and from a number of depths at each station
(see map, page v). During each visit, a single depth-integrated (4.6
m or near bottom to surface) sample was composited from the stations for
phytoplankton identification and enumeration; and during the first visit,
two 18.9-liter depth-integrated samples were composited for algal assays
(stations 1 , 2, and 3 were combined, and stations 4, 5, and 6 were com-
bined). Also each time, a depth-integrated sample was collected from
each of the stations for chlorophyll a analysis. The maximum depths
sampled were 10.4 meters at station 1, 15.5 meters at station 2, 11.9
meters at station 3, 11.3 meters at station 4, 8.8 meters at station 5,
and 7.0 meters at station 6.
The lake sampling results are presented in full in Appendix 0 and
are summarized in the following table.
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6 SITES
STORET CODE 1139
1ST SAMPLING ( 5/ 8/73) 2ND SAMPLING ( 8/ 9/73) 3RD SAMPLING (10/18/73)
6 SITES
6 SITES
PARAMETER
RANGE
MEAN
MEDIAN
RANGE
MEAN
MEDIAN
RANGE
MEAN
MEDIAN
TEMP (C)
13.9
— 15.9
15.3
15.3
17.5
— 27.7
25.9
26.5
17.8
— 20.8
19.7
20.1
0155 OXY (MG/LI
7.0
— 10.8
9.4
9.6
0.2
— 10.0
4.2
3.8
3.6
— 8.4
6.2
6.4
CNDCTVY (MCROMO)
370.
— 540.
467.
500.
342.
— 468.
422.
424.
366.
— 441.
384.
375.
PH (STAND UNITS)
8.0
— 8.5
8.3
8.3
7.3
— 8.7
7.9
7.9
7.4
— 8.1
7.7
7.7
TOT ALK (MG/LI
127.
— 183.
167.
181.
143.
— 240.
161.
155.
162.
— 210.
174.
166.
TOT P (MG/LI
0.04S
— 0.195
0.106
0.084
0.021
— 0.289
0.053
0.035
0.0 3
— 0.128
0.063
0.050
ORTHO P (MG/LI
0.009
— 0.146
0.059
0.037
0.005
— 0.228
0.024
0.008
0.014
— 0.040
0.023
0.021
N02.NO3 (MG/L)
4.620
— 6.670
5.954
6.220
0.600
— 3.830
2.921
3.160
1.340
— 2.140
1.882
2.025
AMMONiA (MG/LI
0.040
— 0.130
0.077
0.060
0.050
— 2.210
0.267
0.090
0.010
— 0.080
0.044
0.040
KJEL N (MG/L)
0.300
— 0.900
0.579
0.600
0.600
— 3.400
1.103
1.000
0.400
— 1.100
0.639
0.600
INORG N (M&/L)
4.740
— 6.750
6.031
6.280
2.530
— 4.090
3.188
3.245
1.380
— 2.190
1.926
2.055
TOTAL N (MG/LI
5.120
— 7.270
6.533
6.860
3.340
— 4.830
4.025
4.070
2.120
— 2.890
2.521
2.510
CHLRPYL A (UG/L
2.9
— 43.5
20.5
21.1
8.4
— 39.5
18.1
14.4
5.3
— 26.3
12.8
10.2
SECCHI (METERS)
0.5
— 1.5
0.9
1.0
1.2
— 1.8
1.6
1.6
0.3
— 0.9
0.5
0.5
a .,
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7
B. Biological characteristics:
1. Phytoplankton —
Sampling Dominant Algal units
Date Genera per ml
05/08/73 1. Centric diatoms 2,476
2. Flagellates 2,459
3. Stephanodiscus . 1,451
4. Meloslra 1,059
5. Euglena .a• 256
Other genera 461
Total 8,162
08/09/73 1. Achnanthes . 963
2. Flagellates 935
3. Stephanodiscus p_. 767
4. Nitzschla .a• 460
5. Cryptornonas . . 321
Other genera 1,019
Total 4,465
10/18/73 1. Melosira p. 483
2. Flagellates 189
3. Aphanlzomenon p_. 141
4. Stephanodiscus . 141
5. Cryptomonas . 106
Other genera 378
Total 1,438
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8
2. Chlorophyll a -
Sampling
Date
05/08/73
Station
Number
01
02
03
04
05
06
01
02
03
• 04
05
06
01
02
03
04
05
06
Chlorophyll -
(pg/l)
19.7
43.5
27.7
22.6
6.9
2.9
8.4
14.8
19.8
14.1
39.5
11.9
6.3
5.3
9.5
10.9
26.3
18.8
1. Autociaved, filtered, and nutrient spiked -
a. Stations 1, 2, and 3 -
Spike (mg/i )
Control
0.050 P
0.050 P + 1 .0 N
1.0 N
Ortho P
Conc. (mg/l )
0.045
0.095
0.095
0.045
Inorganic N
Conc. (mg/i )
5.535
5.535
6.535
6.535
Maximum yield
( mg/i-dry wt. )
16.6
36.5
44.1
15.1
b. Stations 4, 5, and 6 -
Spike (mg/i )
Control
0.050 P
0.050 P + 1.0 N
1.0 N
Ortho P
Conc. (mg/i )
0.020
0.070
0.070
0.020
Inorganic N
Conc. (mg/i )
6.240
6.240
7.240
7.240
Maximum yield
( mg/i-dry wt. )
5.2
23.6
23 . 3
3.8
08/09/73
10/18/73
C. Limiting Nutrient Study:
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9
2. Discussion —
The control yields of the assay alga, Selenastrum capri-
cornutum , indicate that the potential primary productivity
of Shelbyville Reservoir was relatively high at the time
of sampling (05/08/73), especially at stations 1, 2, and 3
(see map, page v). The results also indicate phosphorus
limitation at that time. Note the lack of increase in
yields when only nitrogen was added but the significant
increase in yields when only phosphorus was added.
The reservoir data indicate phosphorus limitation at
all sampling times. The mean inorganic nitrogen/ortho-
phosphorus ratios were 84/1 or greater, and phosphorus
limitation would be expected.
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10
IV. NUTRIENT LOADINGS
(See Appendix E for data)
For the determination of nutrient loadings, the Illinois National
Guard collected monthly near-surface grab samples from each of the
tributary sites Indicated on the map (page v), except for the high
runoff month of March when two samples were collected. Sampling was
begun in June, 1973, and was completed in May, 1974.
Through an interagency agreement, stream flow estimates for the
year of sampling and a “normalized” or average year were provided by
the Illinois District Office of the U.S. Geological Survey for the
tributary sites nearest the lake.
In this report, nutrient loads for sampled tributaries were deter-
mined by using a modification of a U.S. Geological Survey computer
program for calculating stream loadings*. Nutrient loads shown are
those measured minus point-source loads, if any.
Nutrient loads for unsampled “minor tributaries and immediate
drainage” (“ZZ” of U.S.G.S.) were estimated using the means of the
nutrient exports, in kg/km 2 /year, at station B-i, C-i, and H-i and
multiplying the means by the ZZ area in km 2 .
The operators of the Corps of Engineers, Illinois Masonic Home,
and Sullivan wastewater treatment plants provided monthly effluent
samples and corresponding flow data. The operators of Arthur, Atwood,
* See Working Paper No. 175.
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11
± Anonymous, 1972.
* Estimated at 0.3785 m 3 /capita/day.
Bethany, Cerro Gordo School, Urbana-Champaign Sanitary District,
Findlay, Hammond, Lovington, and Windsor treatment plants did not
participate in the sampling program, and nutrient loads were esti-
mated at 1.134 kg P and 3.401 kg N/capita/year.
The nutrient loads shown for the U.S. Industrial Water Supply
Company were calculated using effluent data provided by the Illinois
Environmental Protection Agency (Barganz, 1974); note, however, the
nitrogen load is inorganic nitrogen only.
A. Waste Sources:
1. Known municipal -
Pop. Mean Flow Receiving
Name Served Treatment (m 3 /d) Water
Arthur 2,100 contact stab. 794.8* Kaskaskia River
Atwood 1 ,050 act, sludge 3974* Lake Fork
Bethany 750 act, sludge 283.9* Marrowbone Creek
Cerro Gordo 150 act. sludge 56.8* West Okaw Creek
School
Corps of 10 act. sludge 6.5 Shelbyville
Engineers Reservoir
Findlay 760 contact stab. 287.7* Unnamed Creek
Hammond 730 ponds 276.3* West Okaw Creek
Ill. Masonic 400 trickling 187.2 Jonathan Creek
Home filter
Lovington 1 ,200 act. sludge 454.2* West Okaw Creek
Sullivan 5,000 act. sludge 3,3033.6 Asa Creek
Urbana- 20,000 act. sludge 7,570.0* Copper Slouqh/
Champaign SD Phinney Branch
Windsor 900 act, sludge 340.6* Sand Creek
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2. Known industrial* —
Mean Flow Receiving
Name Product Treatment ( m 3 /d) Water
U.S. md. chemicals coag., 1,892.5 Kaskaskia River
Water Supply settling,
Co., Ficklin + pond
* Barganz, op. cit.
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B. Annual Total Phosphorus Loading - Average Year:
1. Inputs -
kgP/ %of
Source yr total
a. Tributaries (non—point load) —
Kaskaskia River 90,600 49.4
Unnamed Creek (B—i) 825 0.4
Wiiborn Creek 855 0.5
West Okaw Creek 11,005 6.0
Marrowbone Creek 14,345 7.8
Asa Creek 5,110 2.8
Jonathan Creek 6,080 3.3
Whitley Creek 3,945 2.1
Sand Creek 2,365 1.3
b. Minor tributaries & immediate
drainage (non—point load) - 9,100 5.0
c. Known municipal STP’s -
Arthur 2,380 1.3
Atwood 1,190 0.6
Bethany 850 0.5
Cerro Gordo School 170 <0.1
Corps of Engineers <5 <0.1
Findlay 860 0.5
Hammond 830 0.5
Ill. Masonic Home 695 0.4
Lovington 1,360 0.7
Sullivan 5,080 2.8
Urbana-Champaign SD 22,680 12.3
Windsor 1,020 0.6
d. Septic tanks* - 15 <0.1
e. Known industrial -
U.S. md. Water Supply Co. 1,380 0.7
f. Direct precipitation** - 780 0.4
Total 183,520 100.0
2. Outputs -
Lake outlet - Kaskaskia River 63,255
3. Net annual P accumulation - 120,265 kg.
* Estimate based on 60 lakeshore dwellings; see Working Paper No. 175.
** See Working Paper No. 175.
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14
C. Annual Total Nitrogen Loading - Average Year:
L Inputs -
kgN/ %of
Source yr total
a. Tributaries (non—point load) —
Kaskaskia River 1,841,120 48.1
Unnamed Creek (B—l) 33,335 0.9
Wilborn Creek 53,540 1.4
West Okaw Creek 618,930 16.2
Marrowbone Creek 231,580 6.1
Asa Creek 48,310 1.3
Jonathan Creek 200,955 5.2
Whitley Creek 158,770 4.1
Sand Creek 57,095 1 .5
b. Minor tributaries & immediate
drainage (non—point load) - 418,135 10.9
c. Known municipal STP’s -
Arthur 7,140 0.2
Atwood 3,570 0.1
Bethany 2,550 0.1
Cerro Gordo School 510 <0.1
Corps of Engineers 45 <0.1
Findlay 2,585 0.1
Hamond 2,485 0.1
Ill. Masonic Home 985 <0.1
Lovington 4,080 0.1
Sullivan 13,320 0.3
Urbana-Champaign SD 68,020 1.8
Windsor 3,060 0.1
d. Septic tanks* - 640 <0.1
e. Known industrial -
U.S. md. Water Supply Co.** 6,630 0.2
f. Direct precip1tation * - 48,065 1 .2
Total 3,825,455 100.0
2. Outputs —
Lake outlet — Kaskaskia River 2,982,440
3. Net annual N accumulation - 843,015 kg.
* Estimate based on 60 lakeshore dwellings; see Working Paper No. 175.
** Inorganic N only.
See Working Paper No. 175.
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15
D. Mean Annual Non-point Nutrient Export by Subdrainage Area:
Tributary kg P/km 2 /yr kg N/km 2 /yr
Kaskaskia River 69* 1,404
Unnamed Creek (B—l) 25 1,013
Wilborn Creek 20 1,236
West Okaw Creek 25 1 ,397
Marrowbone Creek 95* 1,537
Asa Creek 145* 1 ,372
Jonathan Creek 41 1 ,368
Whitley Creek 33 1,335
Sand Creek 44 1 ,055
* Unusually high export rates indicate possible point-source impact.
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E. Yearly Loading Rates:
In the following table, the existing phosphorus loading
rates are compared to those proposed by Vollenweider (Vollen-
weider and Dillon, 1974). Essentially, his “dangerous” rate
is the rate at which the receiving water would become eutrophic
or remain eutrophic; his “permissible” rate is that which would
result in the receiving water remaining oligotrophic or becoming
oligotrophic if morphometry permitted. A mesotrophic rate would
be considered one between “dangerous” and “permissible”.
Note that Vollenweider’s model may not be applicable to
water bodies with short hydraulic retention times.
Total Phosphorus Total Nitrogen
Total Accumulated Total Accumulated
grams/m 2 /yr 4.12 2.70 85.9 18.9
Vollenweider loading rates for phosphorus
(g/m 2 /yr) based on mean depth and mean
hydraulic retention time of Shelbyville
Reservoir:
“Dangerous” (eutrophic rate) 0.72
“Permissible” (oligotrophic rate) 0.36
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17
V. LITERATURE REVIEWED
Anonymous, 1972. Wastewater treatment works data book. IL Env.
Prot. Agency, Springfield.
Barganz, Ronald M., 1975. Personal communication (point sources
in reservoir drainage; effluent data). IL Env. Prot. Agency,
Springfield.
Forneris, John J., 1973. Personal communication (lake niorphometry).
IL Env. Prot. Agency, Springfield.
Vollenweider, R. A., and P. J. Dillon, 1974. The application of
the phosphorus loading concept to eutrophication research.
Natl. Res. Counsil of Canada Publ. No. 13690, Canada Centre
for Inland Waters, Burlington, Ontario.
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VI. APPENDICES
APPENDIX A
LAKE RANKINGS
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LAKE DATA TO BE USED IN RANKINGS
LAKE MEDIAN MEDIAN 500— MEAN 15— MEDIAN
CODE LAKE NAME TOTAL P INORG N MEAN SEC CIiLORA MIN DO DISS ORTHO P
1703 LAKE 6LOOMINGION 0.050 5.730 464.667 26.200 1 ..800 0.020
1706 LAKE CARLYLE 0.064 1.270 477.889 17.367 11.000 0.032
1708 LAKE CHARLESTON 0.160 4.680 490.667 12.000 8.400 0.065
1711 COFFEEN LAKE 0.032 0.260 456.222 7.700 14.900 0.012
1712 CRA8 ORCHARD LAKE 0.082 0.200 482.222 59.867 13.800 0.013
1714 LAKE DECATUR 0.129 3.750 479.571 43.000 14.500 0.062
1725 LONG LAKE 0.104 1.190 482.661 49.333 8.800 0.398
1726 LAKE LOU YAEGER 0.186 1.600 489.583 10.662 11.400 0.076
1727 LAKE MARIE 0.098 0.370 467.667 39.533 14.700 0.057
1733 PISTAKEE LAKE 0.203 0.310 485.667 75.867 7.000 0.062
1735 REND LAKE 0.071 0.210 471.500 23.533 12.700 0.012
1739 LAKE SHEI8YVILLE 0.062 3.290 461.333 17.161 14.800 0.019
1740 S1L ER LAKE (HIGHLAND) 0.226 0.970 489.500 5.822 14.600 0.057
1742 LAKE SPRINGFIELD 0.109 3.265 483.385 13.013 10.800 0.059
1748 VERMILION LAKE 0.109 4.695 481.500 31.150 14.200 0.050
1750 WONDER LAKE 0.426 0.890 486.000 98.533 7.800 0.132
1751 LAKE STORY 0.072 2.510 459.333 17.250 14.800 0.021
1752 DEPUE LAKE 0.438 4.050 490.000 58.833 7.600 0.276
1753 LAKE SANGCNNIS 0.050 1.970 475.417 19.292 14.500 0.009
1754 LAKE HOLIDAY 0.167 3.135 485.167 51.217 7.200 0.046
1755 FOX LAKE 0.219 0.375 486. 167 63.850 8.800 0.083
1756 GRASS LAKE 0.301 0.820 481.000 83.500 5.900 0.093
1757 EAST LOON LAKE 0.076 0.120 450.000 22.300 14.900 O. O IH
1758 SLOCUM LAKE 0.865 0.200 487.333 221.100 5.800 0.362
1759 CEDAR LAKE 0.029 0.170 400.333 5.767 12.800 0.013
1761 LAKE WEP4ATUK 0.069 1.770 466.333 7.967 14.500 0.031
1762 RACCOON LAKE 0.106 0.310 484.333 19.217 13.800 0.020
1763 8ALUWIN LAKE 0.044 0.140 461.161 11.333 13.200 0.007
-------
LAPcE DATA TO BE USED IN RANKINGS
LAKE
CODE
LAKE
NAME
MEDIAN
TOTAL P
MEDIAN
INORG N
500—
MEAN SEC
MEAN
CMLORA
15-
MIN DO
MEDIAN
DIsS O ThO P
1764
LAKE
VANDALIA
0.116
0.480
478.111
11.276
14.800
0.023
176S
OLD
BEN MINE
RESERVOIR
0.930
0.205
478,333
31.433
11.200
0.575
1766
HORSESHOE LAKE
0.127
0.705
482.833
182.250
6.dOO
0.O1
-------
PERCENT OF LAKES WITH HIGHER VALUES (NUMBER OF LAKES WITH r (IGHER VALUES)
LAKE
CODE
LAKE NAME
MEDIAN
TOTAL P
MEDIAN
INORG N
500—
MEAN SEC
MEAN
CHLORA
15—
MIN
DO
MEDIAN
DISS ORTHO P
INDEX
NO
1703
LAKE 8LOOHINGTON
88 ( 26)
0 (
0)
0 C 24)
47 C 14)
13 C
2)
68
C 20)
296
1706
LAKE CARLYLE
63 C 19)
40 (
12)
63 C 19)
63 C 19)
63 C
19)
53
C 16)
345
1708
LAKE CHARLESTON
37 C 11)
7 C
2)
0 C 0)
77 C 23)
77 C
23)
27
8)
225
1711
COFFEEN LAKE
97 ( 29)
77 C
23)
93 C 28)
93 I 28)
2
0)
92
C 27)
454
1712
CRAB ORCHARD LAKE
67 C 20)
90 C
27)
43 C 13)
20 C 6)
42
12)
85
C 25)
347
1714
LAKE DECATUR
40 C 12)
13 C
4)
53 I 16)
33 C 10)
30 6
8)
32
C 9)
201
1725
LONG LAKE
7 6 2)
43 1
13)
40 C 12)
30 C 9)
72 C
21)
3
6 1)
195
172t
LAKE LOU YAEGER
30 ( 9)
37 6
11)
7 6
2)
87 C 26)
57 6
17)
23
C 7)
241
1727
LAKE MARIE
60 C 18)
68 C
20)
73 C
22)
37 C 11)
23 C
7)
42
( 12)
303
1733
PISTAKE LAKE
27 6 8)
68 C
20)
23 C
7)
13 C 4)
90 (
27)
32
C 9)
253
1735
REND LAKE
77 ( 23)
80 C
24)
70 1
21)
50 C 15)
53 6
16)
92
C 27)
422
1739
LAKE SHELOYVILLE
83 C 25)
17 C
5)
83 6
25)
70 C 21)
13 C
2)
73
C 22)
339
1740
SILVER LAKE (HIGHLAND)
20 ( 6)
47 C
14)
10 1
3)
97 C 29)
13 1
2)
42
C 12)
229
1742
LAKE SPRINGFIELD
53 C 16)
20 C
6)
33 C
10)
73 C 22)
67 C
20)
37
C 11)
283
1748
VERMILION LAKE.
SO 6 15)
3
1)
47 1
14)
43 C 13)
37 6
11)
47
1 14)
227
1750
WONDER LAKE
13 ( 4)
50 (
15)
20 (
6)
7 C 2)
80 C
24)
13
1 4)
183
1751
LAKE STORY
73 C 22)
27 C
8)
90 C
27)
67 C 20)
13 C
2)
63
( 19)
333
1752
DEPUE LAKE
10 C 3)
10 C
3)
3 6
1)
23 C 7)
83
25)
10
I 3)
139
1753
LAKE SANGCHRIS
88 C 26)
30 C
9)
07 C
20)
57 C 17)
30 C
8)
97
C 29)
369
l754
LAKE HOLIDAY
33 C 10)
23 C
fl
27 C
8)
27 C 8)
87 C
26)
50
C 15)
247
1755
FOX LAKE
23 C 7)
63 C
19)
17 C
5)
17 C 5)
72 C
21)
20
C 6)
212
1756
GRASS LAKE
17 C S)
53 I
16)
50 C
15)
10 6 3)
97 C
29)
17
C 5)
244
1757
EAST LOON LAKE
70 C 21)
100 6
30)
97 1
29)
53 C 16)
2 C
0)
77
( 23)
3V9
1758
SLOCUM LAKE
3 C I)
87 C
26)
I] C
4)
0 C 0)
100 C
30)
7
C 2)
210
1759
CEDAR LAKE
100 ( 30)
93 C
28)
100 C
30)
100 C 30)
50 C
IS)
85
C 25)
528
1761
LAKE EMATUK
80 ( 24)
33 C
10)
17 C
23)
90 C 27)
30 (
8)
57
C 17)
361
1762
RACCOON LAKE
57 C 17)
73 C
22)
30 C
9)
1763 BALDWIN LAKE
93 C 28) 97 C 29) 87 C 26 80 C 24) 47 ( I’.) 100 C 3D)
50’.
-------
PERCENT OF
LAKES WITH HIGHER VALUES (NUMBER OF
LAKES WITH HIGHER VALUES)
LAKE
CODE
LAKE
NAME
MEDIAN
TOTAL P
MEDIAN
INORG
N
500—
MEAN
SEC
P4€AN
CHLORA
15-
MIN
DO
MEDIAN
DISS ORTr1O
P
INOtX
NO
1764
LAKE
VANDALIA
47 ( 14)
60 (
18)
60
( 18)
83 ( 25)
13 (
2)
60 ( 18)
323
1765
OLD
BEN MINE RESERVOIR
0 ( 0)
83 (
25)
57
( 17)
40 ( 12)
60 1
18)
0 1 0)
2 .0
1766
HORSESHOE LAKE
43 ( 13)
57 (
17)
37
( 11)
3 1 1)
93 1
28)
80 1 24)
313
-------
LAKES RANJ EO BY INDEX NOS.
RANK LAKE CODE LAKE NAME INDEX NO
1 1759 CEDAR LAKE 528
2 1763 BALDWIN LAKE 504
3 1711 COFFEEN LAKE 454
4 1735 REND LAKE 422
5 1757 EAST LOON LAKE 399
6 1753 LAKE SANGC,IRIS 369
7 1761 LAKE WEMATUK 367
8 1712 CRAB ORCHARD LAKE 347
9 1706 LAKE CARLYLE 345
10 1739 LAKE SHELBYVILLE 339
11 1751 LAKE STORY 333
12 1762 RACCOON LAKE 330
13 176’. LAKE VANDALIA 323
14 1766 HORSESHOE LAKE 313
15 1727 LAKE MARIE 303
16 1703 LAKE BLOOMINGTON 296
17 1742 LAKE SPRINGFIELD 283
18 1733 PISTAKEE LAKE 253
19 1754 LAKE HOLIDAY 247
20 1756 GRASS LAKE 244
21 1726 LAKE LOU YAEGER 241
22 1765 OLD 8EN MINE RESERVOIR 240
23 1740 SILVER LAKE (HIGHLAND) 229
24 1748 VENMILION LAKE 227
25 1708 LAKE CHARLESTON 225
26 1155 FOX LAKE 212
27 1758 SLOCUM LAKE 210
28 lii ’. LAKE DECATUR 201
-------
LAKES RANKED BY INDEA NOS.
RANK LAKE CODE LAKE NAME INDEX NO
29 1725 LONG LAKE 195
30 1750 WONDER LAKE 183
31 1752 DEPUE LAKE 139
-------
APPENDIX B
CONVERSIONS FACTORS
-------
CONVERSION FA(;TORS
Hectares x 2.471 = acres
Kilometers x 0.6214 = miles
Meters x 3.281 = feet
Cubic meters x 8.107 x = acre/feet
Square kilofrieters x 0.3861 = square miles
Cubic meters/sec x 35.315 = cubic feet/sec
Centimeters x 0.3937 = inches
Kilograms x 2.205 = pounds
Kilograms/square kilometer x 5.711 = lbs/square mile
-------
APPENDIX C
TRIBUTARY FLOW DATA
-------
TRIBUTARY FLOW INFORMATION FOR ILLINOIS 10/23/75
LAKE CODE 1739 LAKE SHELBYVILLE
TOTAL DRAINAGE AREA OF LAKE(SO KM) 2729.9
SUB-DRAINAGE NORMALIZED FLOWS (CMS)
TRIdUTARY AREA(SQ KM) JAN FEB MAR APR MAY JUN JUL AUG SEP OCT NOV DEC MEAN
1739*1 2729.9 20.16 26.02 34.83 36.53 39.08 21.10 13.90 7.79 6.09 7.50 10.34 12.0* *9.57
1739A2 1310.5 9.68 12.80 16.59 17.61 18.83 10.08 6.48 3.48 2.63 3.34 4.73 5.61 9.30
1739 I 32.9 0.20 0.32 0.39 0.40 0.31 0.27 0.16 0.08 0.05 0.06 0.09 0.11 0.20
1739C1 43.3 0.27 0.42 0.51 0.53 0.41 0.35 0.21 0.11 0.07 0.08 0.12 0.14 0.21
173901 442.9 3.00 4.28 5.44 5.64 4.45 3.65 2.26 1.19 0.87 1.00 1.40 1.64 2.89
1739E 1 150.7 0.98 1.46 1.81 1.87 1.47 1.23 0.74 0.39 0.27 0.30 0.44 0.52 0.95
1739F 1 35.2 0.22 0.35 0.42 0.43 0.33 0.29 0.17 0.09 0.06 0.06 0.09 0.11 0.22
173961 146.9 0.96 1.43 1.77 1.83 1.44 1.20 0.73 0.38 0.27 0.29 0.43 0.51 0.93
1739H1 118.9 0.77 1.16 1.43 1.48 1.16 0.97 0.59 0.31 0.21 0.23 0.35 0.41 0.75
1739J* 54.1 0.34 0.53 0.65 0.66 0.52 0.44 0.26 0.13 0.09 0.10 0.15 0.18 0.34
1739ZZ 393.7 3.77 3.28 5.83 6.09 10.17 2.61 2.31 1.63 1.55 2.04 2.54 2.78 3.73
SUMMARY
TOTAL DRAINAGE AREA OF LAKE © 2729.9 TOTAL FLOW IN a 235.38
SUM OF SUB—DRAINAGE AREAS = 2729.1 TOTAL FLOW OUT a 235.34
MEAN MONTHLY FLOWS AND DAILY FLOWSCMS
TRIBUTARY MONTH YEAR MEAN FLOW DAY FLOW DAY FLOW DAY FLOW
1739*1 6 73 39.36 2 39.36
7 73 40.49 7 46.44
8 73 60.88 4 61.73
9 73 51.54 9 61.16
10 73 11.69 14 0.02
11 73 19.54 3 1.93
12 73 44.74 1 42.76
1 74 38.79 5 52.67
2 74 128.84 3 75.32
3 74 108.74 2 139.04 16 97.13
4 74 24.47 6 20.81
5 74 34.26 4 21.32
1739A2 6 73 26.50 2 8.78
7 73 31.15 7 IS. 18
8 73 13.34 4 36.25
9 73 1.27 9 0.01
10 73 2.46 13 1.73
11 73 5.18 3 3.45
12 73 31.71 1 17.27
I 74 56.35 4 30.58
2 7’. 28.60 3 40.49
3 74 32.28 2 44.17 16 19.91
4 74 32.28 6 35.96
5 74 39.08 4 9.23
-------
TRIBUTARY FLOW INFORMATION FOR ILLINOIS 10/23/75
LAKE CODE 1739 LAKE SHELBYVILLE
MEAN MONTHLY FLOWS AND DAILY FLOWS(CMS)
TRIBUTARY MONTH YEAR MEAN FLOW DAY FLOW DAY FLOW DAY FLOW
173981 6 73 0.91 2 0.42
7 73 0.79 7 0.18
8 73 0.11 4 0.25
9 73 0.00 9 0.01
10 73 0.03 13 0.03
11 73 0.11 3 0.01
12 73 0.59 1 0.31
1 74 1.44 5 0.54
2 74 0.57 3 0.28
3 74 0.76 2 0.74 16 0.68
4 74 1.02 6 1.27
5 74 2.01 4 0.15
1739C 1 6 73 1.19 2 0.54
7 73 1.05 7 0.24
8 73 0.14 4 0.34
9 13 0.00 9 0.01
10 73 0.03 13 0.05
11 73 0.15 3 0.01
12 73 0.79 1 0.42
1 74 19.26 5 0.71
2 74 0.74 3 0.37
3 74 0.99 2 0.96 16 0.91
4 74 1.33 6 1.70
5 74 2.66 4 0.20
173901 6 73 9.60 2 3.17
7 73 10.87 7 5.27
8 73 4.56 4 12.37
9 73 0.42 9 0.48
10 73 0.74 13 0.51
11 73 1.53 3 1.02
12 73 9.29 1 5.04
I 74 17.47 5 9.49
2 74 9.57 2 13.51
3 74 10.53 2 14.53 16 14.53
4 74 10.36 6 11.50
5 74 13.90 4 2.18
1739E 1 6 73 4.08 2 1.90
7 73 3.60 7 1.76
8 73 1.47 7 4.02
9 73 0.13 9 0.15
10 73 0.22 13 0.16
11 73 0.48 3 0.31
12 73 2.97 1 1.61
1 74 5.69 5 3.09
2 74 3.26 3 4.62
3 74 3.51 2 4.84 16 4.84
4 74 3.43 6 3.82
5 74 4.59 4 0.71
-------
TRIBUTARY FLOW INFORHATIOP4 FOR ILLINOIS 10/23/75
LAKE CODE 1739 LAKE SHEL YVILLE
MEAN MONTHLY FLOWS AND DAILY FLOWS(CMS)
TRIBUTARY MONTH YEAR MEAN FLOW DAY FLOW DAY FLOW DAY FLOW
1739F1 6 73 0.96 2 0.45
7 73 0.85 7 0.19
8 73 0.12 4 0.21
9 73 0.00 8 0.01
10 73 0.03 13 0.03
11 73 0.12 3 0.01
12 73 0.65 1 0.34
1 74 1.56 4 0.57
2 74 0.59 2 0.31
3 74 0.79 2 0.79 16 0.74
4 74 1.10 6 1.36
5 74 2.15 4 0.16
173901 6 73 3.99 2 1.84
7 73 3.51 7 1.70
8 73 1.44 4 3.96
9 73 0.13 8 0.15
10 73 0.22 13 0.15
11 73 0.48 3 0.31
12 73 2.92 1 1.59
1 74 5.58 4 3.03
2 74 3.20 2 4.50
3 74 3.43 2 4.73 16 4.73
4 74 3.37 6 3.74
5 74 4.50 4 1.08
1739 1 11 6 73 3.23 2 1.50
7 73 2.83 7 1.36
8 73 1.16 7 3.17
9 73 0.10 8 0.12
10 73 0.17 13 0.12
11 - 73 0.37 3 0.25
12 73 2.32 1 1.25
1 74 4.47 5 2.44
2 74 2.61 2 3.65
3 74 2.78 2 3.82 16 3.82
4 74 2.72 6 3.00
5 74 3.62 4 0.85
1739)1 6 73 1.47 2 0.68
7 73 1.30 7 0.28
8 73 0.18 4 0.42
9 73 0.01 8 0.01
10 73 0.04 13 0.06
11 73 0.19 3 0.02
12 73 1.02 1 0.51
I 74 2.44 5 0.91
2 74 0.93 3 0.48
3 74 1.25 2 1.22 16 1.13
4 74 1.70 6 2.12
5 74 3.34 4 0.25
-------
TRIBUTARY FLOW INFORMATION FOR ILLINOIS 10/23/75
LAKE CODE 1739 LAKE SHELBYVILLE
MEAN MONTHLY FLOWS AND DAILY FLOWS(CMS)
TRIBUTARY MONTH YEAR MEAN FLOW DAY FLOW DAY FLOW DAY FLOW
1739ZZ 6 73 8.64 2 2.86
7 73 9.77 7 4.73
8 73 4.08 4 11.10
9 73 0.37 9 0.42
10 73 0.65 14 0.45
11 73 0.06 3 0.01
12 73 8.30 1 4.50
1 74 15.72 5 8.52
2 74 8.41 3 11.44
3 74 9.46 2 12.71 16 8.61
4 74 9.63 6 10.85
5 74 12.74 4 2.49
-------
APPENDIX D
PHYSICAL and CHEMICAL DATA
-------
STORET RETRIEVAL DATE 75/10/23
173901
39 2’. 30.0 088 46 30.0
LAXE SHEL8YVILLE
17173 ILLINOIS
I 1EPALES 2111202
3 0037 FEET DEPTH
00010 00300 00077 00094 00400 00410 00610 00625 00630 00671
DATE TIME DEPTH WATER DO TRANSP CNDUCTVY PH 7 ALK NI43—N TOT KJ€L NO2LNO3 P 1405—015
FROM OF TEMP SECCHI FIELD CACO3 TOTAL N N—TOTAL ORTISO
TO DAY FEET CENT MG/L INCHES MICROMHO SU MG/I M(i/L NG/L M6/L MG/L P
73/05/08 09 30 0000 14.7 60 500 8.30 182 0.080 0.700 6.270 0.020
09 30 0006 14.7 9.6 500 8.30 182 0.060 0.500 6.220 0.017
09 30 0015 14.7 9.9 500 8.30 183 0.060 0.600 6.130 0.018
09 30 0024 14.6 9.8 540 8.30 181 0.060 0.900 6.080 0.018
09 30 0033 14.5 9.2 540 8.10 182 0.070 0.500 6.180 0.026
73/08/09 11 35 0000 26.5 72 436 8.00 158 0.060 0.800 3.280 0 .808
11 35 0005 26.5 5.0 436 7.80 157 0.060 0.700 3.180 0. 106
11 35 0010 26.3 3.0 436 7.70 158 0.070 0.800 3.220 8.006
11 35 0015 26.2 2.6 437 7.60 158 0.090 0.700 3.160 0.101
11 35 0025 26.0 1.4 435 7.40 160 0.110 0.800 3.100 0.008
11 35 0034 23.9 1.0 456 7.40 190 0.690 1.500 1.840 1.014
73/10/la 16 20 0000 20.4 18 378 7.70 167 0.050 0.800 2.090 0.014
16 20 0010 20.5 5.2 380 7.50 167 0.050 0.600 2.140 0.014
16 20 0020 20.3 4.6 377 7.50 169 0.040 0.400 2,080 S.S15
00665 32217
DATE TIME DEPTH PHOS-TOT CHLRPHYL
FROM OF A
TO DAY FEET MG/I P UG/L
73/05/08 09 30 0000 0.069 19.7
09 30 0006 0.060
09 30 0015 0.063
09 30 0024 0.060
09 30 0033 U.071
73/06/09 11 35 0000 0.023
11 35 0005 0.023
11 35 0010 0.021
11 35 0015 0.023
11 35 0025 0.024
11 35 0034 0.034
73/10/18 16 20 0000 0.035 6.3
16 20 0010 0.036
lb 20 0020 0.036
-------
STORET RETRIEVAL DATE 75/10/23
173902
39 26 30.0 088 45 40.0
LAKE SHEL8’VVILLE
17173 ILLINOIS
11EPALES 2111202
3 0054 FEET DEPTH
00010 00300 00077 00094 00400 00410 00610 00625 00630 00671
DATE TIME DEPTH WATER DO TRANSP CNDUCTVY PH 1 AL NH3—N TOT kJ(L 2 O3 PHOS—O IS
FROM OF TEMP SECCHI FIELD CACO3 TOTA l. N N—TOTAL ORTHO
TO DAY FEET CENT MG/L INCHES MICRO+IHO SU MG/I MG/L MG/I MG/I M /L P
73/05/08 10 10 0000 15.3 40 500 8.50 182 0.070 0.800 4.300 0.009
10 10 0006 15.3 10.8 500 8.50 181 0.061 0.000 6.240 0.010
10 10 0015 15.3 10.7 500 8.50 182 0.060 0.700 6.290 0.011
10 10 0025 15.2 10.6 500 8.40 182 0.060 0.600 6.300 0.013
10 10 0037 15.0 10.3 500 8.20 181 0.070 0.611 6.390 0.018
10 10 0050 13.9 7.0 500 8.20 183 0.120 0.511 6.410 0.041
73/08/09 12 05 0000 27.1 68 438 8.30 158 0.070 1.000 3.220 0.005
12 05 0005 27.1 6.8 437 8.30 158 0.060 0.810 3.220 1.117
12 05 0015 27.0 6.0 436 8.00 157 0.060 0.900 3.220 0.009
12 05 0025 26.1 1.8 424 7.50 155 0.070 0.800 3.280 0.014
12 05 0040 23.2 0.2 457 7.50 199 1.330 2.700 1.640 0.094
12 05 0051 17.5 0.5 423 7.50 240 2.210 3.400 0.610 0.228
73/10/16 15 20 0000 20.8 36 379 7.50 165 0.060 0.700 2.061 0.014
15 20 0015 20.4 3.8 375 7.40 166 0.080 0.600 2.090 0.0)5
15 20 0040 20.1 3.6 376 7.40 166 0.080 0.600 2.040
00665 32217
DATE TIME DEPTH PHOS-TOT CHLRPHYL
FROM OF A
TO DAY FEET MG/I P UG/L
73/05/08 10 10 0000 0.045 43.5
10 10 0006 0.079
10 10 0015 0.080
10 10 0025 0.069
10 10 0037 0.075
10 10 0050 0.091
73/08/09 12 05 0000 0.023 14.8
12 05 0005 0.025
12 05 0015 0.028
12 05 0025 0.030
12 05 0040 0.161
12 05 U051 0.289
73/10/18 15 20 0000 0.043 5.3
15 20 0015 0.040
15 20 0040 0.044
-------
STORET RETRIEVAL DATE 75/10/23
173903
39 27 30.0 088 42 40.0
LAP E SHEL8YVILLE
17173 ILLINOIS
IIEPALES 2111202
3 0035 FEET DEPTH
00010 00300 00077 00096 00400 00410 00610 00625 00630 00671
DATE TIME DEPTH WATER 00 TRANSP CNDuCTVY PH 7 ALK NH3—N TOT KJEL N02&N03 PHOS—OIS
FROM OF TEMP SECCHI FIELD CACO3 TOTAL N N—TOTAL ORTHO
TO DAY FEET CENT MG/L INCHES HICROMHO SO M(,/L MG/L MG/L M6/L MG/L P
73/05/08 10 ‘.0 0000 15.2 40 500 8.40 183 0.050 0.600 6.330 0.029
10 40 0006 15.2 10.3 520 8.40 182 9.050 0.600 6.410 0.029
10 40 0015 15.1 10.6 510 8.30 183 0.050 0.500 6.360 0.029
10 40 0022 15.0 10.0 520 8.30 183 0.060 0.600 6.970 0.030
10 40 0031 14.8 8.8 500 8.50 183 0.080 0.600 6.670 0.037
73/08/09 15 00 0000 26.9 62 429 8.30 154 0.050 1.300 3.220 0.015
15 00 0005 26.9 6.6 429 8.20 151 0.060 0.600 3.230 0.005
15 00 0015 26.9 6.4 429 7.90 150 0.090 0.700 2.810 0.010
IS 00 0025 25.9 2.2 414 7.30 152 0.160 0.700 2.780 0.015
15 00 0039 23.8 0.8 417 8.00 174 0.790 1.500 1.880 0.035
73/10/18 15 00 0000 20.5 11 373 7.70 162 0.030 0.700 1.970 0.022
15 00 0005 20.’. 6.6 374 7.60 162 0.030 0.500 2.020 0.0)6
15 00 0015 20.3 6.4 370 7.60 166 0.010K 0.400 2.050 0.014
15 00 0021 20.2 6.2 372 7.70 162 0.030 0.400 2.040 •.119
00665 32217
DATE TIME DEPTH PHOS—TOT CHLRPHYL
FROM OF A
TO DAY FEET HG/L P UG/L
73/05/08 10 40 0000 0.080 27.7
10 40 0006 0.08’.
10 40 0015 0.077
10 40 0022 0.076
10 40 0031 0.080
73/08/09 15 00 0000 0.032 19.8
15 00 0005 0.027
15 00 0015 0.029
15 00 0025 0.035
15 00 0039 0.06S
73/10/18 15 00 0000 0.050 9.S
15 00 0005 0.051
15 00 0015 0.023
15 00 0021 0.050
K VALUE KNOWN TO dF.
LESS THAN INDICATED
-------
STORET RETRIEVAL DATE 75/10/23
173904
39 31 05.0 088 42 05.0
LAKE SHEL8YVILLE
17139 ILLINOIS
1 IEPAL€S 2111202
3 0039 FEET DEPTH
00010 00300 00077 00094 00400 00410 00610 00625 00630 00671
DATE TIME DEPTH WATER DO TRANSP CNDUCTVY PH T ALK NH3—N TOT KJEL N02&N03 PHOS—DIS
FROM OF TEMP SECCHI FIELD CACO3 TOTAL N N—TOTAL ORTP4O
TO L)AY FEET CENT PIG/L INCHES HICRONHO SU MG/L MG/L HG/L MG/L MG/L P
73/05/08 11 10 0000 15.6 36 460 8.30 170 0.040 0.600 6.120 0.070
11 10 0006 15.6 9.6 480 8.30 170 0.040 0.300 6.080 0.070
11 10 0015 15.5 9.5 480 8.30 170 0.040 0.600 6.030 0.067
11 10 0025 15.5 8.3 460 8.40 172 0.050 0.600 6.300 0.065
11 10 0035 15.5 9.5 480 8.40 114 0.050 0.600 6.370 0.062
73/08/09 15 25 0000 27.1 62 422 8.30 149 0.090 1.000 3.100 0.007
15 25 0005 27.1 7,4 421 8.30 149 0.070 0.700 3.180 0.008
15 25 0015 27.1 7,2 420 8.00 146 0.080 0.800 3.260 0.014
15 25 0025 25.6 1.6 402 7.40 151 0.260 0.900 3.160 0.038
15 25 0037 23.8 0.6 342 7.50 143 0.440 1.200 2.420 0.043
73/10/18 14 40 0000 19.9 20 370 7.90 166 0.030 0.600 2.030 0.027
14 40 0015 19.6 6.4 367 7.80 166 0.070 0.600 1.900 0.032
14 40 0023 19.5 6.4 366 7.80 163 0.040 0.500 1.940 0.030
00665 32217
DATE TIME DEPTH PHOS—TOT CHLRPHYL
FROM OF A
TO DAY FEET MG/L P UG/L
73/05/08 11 10 0000 0.122 22.6
11 10 0006 0.111
11 10 0015 0.096
11 10 0025 0.110
11 10 0035 0.131
73/08/09 15 25 0000 0.035 14.1
15 25 0005 0.036
15 25 0015 0.041
15 25 0025 0.066
15 25 0037 0.087
73/10/18 14 40 0000 0.061 10.9
14 40 0015 0.072
14 40 0023 0,060
-------
STORET RETRIEVAL DATE 75/10/23
173905
39 33 05.0 088 38 10.0
LAKE SHELBYVILLE
17139 ILLINOIS
11EPALES 2111202
3 0029 FEET OEPTH
00010 00300 00077 00094 00400 00410 00610 00625 -10630 10671
DATE TIME DEPTH WATER DO TRANSP CNDUCTVY PH T ALK NH3—N TOT N021.N03 I0Sm0IS
FROM OF TEMP SECCHI FIELD CACO3 TOTAL N N—TOTM. 0 THO
TO DAY FEET CENT M6/L INCHES MICRONHO SI) MG/L NG/L /L M6 /L ‘L P
73/05/08 11 30 0000 18 370 8.00 127 0.130 0.510 4.810 0.146
11 30 0006 15.9 7.7 370 8.00 127 0.130 0.501 4.750 0.145
11 30 0015 15.9 9.9 370 8.00 128 0.120 1.500 4.730 0.145
11 30 0025 15.9 8.1 380 8.10 129 0.120 0.500 4.620 0.142
73/08109 15 50 0000 27.3 56 400 8.20 145 0.080 1.200 3.100 0.007
15 50 0005 27.3 10.0 403 8.70 148 0.060 1.100 3.060 0.008
15 50 0015 27.2 9.0 402 7.50 153 0.100 1.100 3.250 0.027
15 50 0029 24.4 2.2 468 7.50 198 0.260 1.000 3.830 0.061
73/10/18 16 55 0000 19.2 18 438 8.10 210 0.040 0.700 1.500 0.021
16 55 0005 19.1 8.4 436 8.10 205 0.040 0.700 1.420 0.028
16 55 0017 18.5 8.0 441 7.90 200 0.040 0.800 1.340 0.026
00665 32217
DATE TIME DEPTH P 1105—TOT CHLRPHYL
FROM OF A
TO DAY FEET MG/L P UG/L
73/05/08 11 30 0000 0.195 6.9
11 30 0006 0.184
11 30 0015 0.188
11 30 0025 0.180
73/08/09 15 50 0000 0.049 39.5
15 50 0005 0.049
15 50 0015 0.062
15 50 0029 0.119
73/10/18 16 55 0000 0.092 26.3
16 55 0005 0.097
16 55 0017 0.128
-------
STORET RETRIEVAL DATE 75/10/23
173906
39 34 15.0 088 43 15.0
LAKE SHELBYVILLE
17139 ILLINOIS
1 IEPALES 2111202
3 0025 FEET DEPTH
00010 00300 00077 00094 00400 00410 00610 00625 00630 00671
DATE TIME DEPTH WATER DO TRANSP CNDUCTVY PH 1 ALK NH3—N TOT KJEL N024.N03 PHOS—DIS
FROM OF TEMP SECCHI FIELD CACO3 TOTAL N N—TOTAL ORTtIO
TO DAY FEET CENT MG/L INCHES MICROMHO SU MG/I MG/L MG/L MG/L M6/L P
73/05/08 11 50 0000 15.9 20 400 8.00 140 0.120 0.500 5.510 0.111
11 SO 0006 15.8 8.7 380 8.00 137 0.120 0.600 5.170 0.110
11 50 0015 15.8 8.6 380 8.00 138 0.110 0.400 5.510 0.106
11 50 0021 15.8 9.0 390 8.00 140 0.110 0.500 5.540 0.113
73/08/09 16 20 0000 27.7 48 404 8.60 152 0.060 1.200 3.160 0.007
16 20 0005 27.0 8.0 396 8.50 149 0.100 1.100 3.060 0.007
16 20 0015 26.2 6.0 392 7.60 149 0.160 1.100 3.020 0.008
16 20 0023 24.0 4.6 417 8.10 179 0.210 1.000 3.160 0.012
73/10/18 14 25 0000 18.0 11 370 8.00 183 0.040 1.100 1.560 0.037
14 25 0006 17.8 8.4 368 8.00 181 0.030 0.800 1.590 0.040
00665 32217
DATE TIME DEPTH P 1105-TOT CHLRPHYL
FROM OF A
TO DAY FEET MG/L P U6/L
73/05/08 11 50 0000 0.152 2.9
11 50 0006 0.144
11 50 0015 0.142
11 50 0021 0.146
73/08/09 16 20 0000 0.046 11,9
16 20 0005 0.041
16 20 0015 0.035
16 20 0023 0.046
73/10/18 14 25 0000 0.104 18.8
14 25 0006 0.104
-------
APPENDIX E
TRIBUTARY and WASTEWATER
TREATMENT PLANT DATA
-------
STORET RETRiEVAL DATE 75/10/23
1739A1
39 24 20.0 088 47 00.0
KASKASKIA RIVER
17081 SHELBY Co MAP
0/LAKE St1EL YVILLE
H Y 16 BRDG Ar E EDGE OF SHELBYVILLE
11EPALE$ 2111204
4 0000 FEET DEPTH
00630 00625 00610 00671 0066i
DATE TIME DEPTH NO2 NO3 TOT KJEL NH3-N PHOS—DIS PHOS-TOT
FROM OF N—TOTAL N TOTAL ORTHO
TO L AY FEET MG/L MG/L MG/I MG/L P MG/L P
73/06/02 10 20 5.500 1.320 0.150 0.009 0.035
73/07/07 10 39 3.500 2.700 0.210 0.027 0.050
73/08/04 10 20 1.500 2.730 0.310 0.022 0.027
73/09/09 09 45 2.200 1.800 0.092 0.010 0.030
73/10/14 09 00 1.920 1.100 0.240 0.040 0.075
73/11/03 10 35 2.100 0.400 0.052 0.019 0.173
73/12/01 10 10 2.000 0.400 0.016 0.028 0.190
74/01/05 10 45 1.920 0.700 0.082 0.024 0.050
74/02/03 09 15 4.620 2.000 0.155 0.080 0.105
74/03/02 10 30 7.700 1.800 0.105 0.095 0.210
74/03/16 09 30 6.200 0.700 0.070 0.080 0.118
74/04/06 09 30 6.000 0.800 0.075 0.075 0.080
74/05/04 15 15 6.400 0.100K 0.030 0.040 0.050
r VAL(J SNOWN [ 0 d
LtSS THAN 1”4DICATED
-------
STORET RETRIEVAL DATE 75/10/23
1 739A2
39 34 20.0 088 32 00.0
KASKASKIA RIVER
17 MOULTRIE Co MAP
1/LAKE SHELBYVILLE
H Y 121 B DG 1 MI N OF ALLENVILLE
11EPALES 2111204
4 0000 FEET DEPTH
00630 00625 00610 00671 00665
DATE TIME DEPTH NO2 NO3 TOT KJEL NH3—N PHOS—DIS PHOS-TOT
FROM OF N-TOTAL N TOTAL ORTHO
TO DAY FEET MG/L MG/L MG/L MG/L P MG/L P
73/06/02 12 50 7.400 2.000 0.079 0.126 0.185
73/07/07 13 51 7.500 1.260 0.068 0.130 0.230
73/08/0 ’. 11 45 4.000 2.520 0.113 0.120 0.185
73/09/07 13 20 1.640 1.890 0.097 0.260 0.360
73/10/13 17 30 2.900 0.970 0.039 0.357 0.450
73/11/03 11 15 2.500 0.700 i).048 0.410 0.630
73/12/01 10 50 5.500 0.100K 0.020 0.144 0.330
74/01/04 14 30 8.300 0.300 0.032 0.076 0.085
74/02/03 11 45 7.500 0.500 0.040 0.100 0.125
74/03/02 10 30 5.400 1.200 0.210 0.130 0.190
74/03/16 11 00 7.300 0.900 0.035 0.110 0.250
74/04/06 10 45 - 6.600 0.900 0.035 0.105 0.230
74/05/04 15 50 7.400 2.700 0.340 0.970 1.600
K VALUE r(NO N TO
LtSS THAN INDICATED
-------
STORET RETRIEVAL DATE 75/10/23
1 739B1
39 34 50.0 088 45 10.0
UNNAMED CP EEtc
17 SHELBY Co MAP
T/LAKE SHELdYVILLE
HWY 2 BROG 3.4 MI N OF FINDLAY
11EPALES 2111204
4 0000 FEET DEPTH
00630 00625 00610 00671 00665
DATE TIME DEPTH N02&N03 TOT KJEL NH3—N PHOS—DIS PHOS—TOT
FROM OF N-TOTAL N TOTAL ORTHO
TO DAY FEET MG/L MG/L P46/I M6/L P MG/L P
73/06/02 10 50 6.500 0.690 0.052 0.042 0.075
73/07/07 11 35 9.100 0.730 0.126 0.039 0.075
73/08/04 10 50 5.200 1.500 0.039 0.054 0.080
73/09/09 10 15 0.530 1.200 0.039 0.220 0.300
73/10/13 17 00 0.340 0.900 0.028 0.273 0.320
73/11/03 11 30 0.126 0.600 0.052 0.077 0.210
73/12/01 10 40 4.600 0. 100K 0.024 0.036 0.185
74/01/05 11 15 5.800 0.200 0.020 0.028 0.030
74/02/03 09 45 5.600 1.000 0.275 0.037 0.050
74/03/02 11 20 5.300 1.200 0.160 0.070
74/03/lb 10 00 5.400 1.100 0.100 0.030 0.110
74/04/06 10 00 7.680 0.500 0.025 0.035 0.070
74/0 /04 16 05 3.700 0.210 0.210 0.020 0.020
K VALUE KNOWN TO BE
LESS THAN INDiCATED
-------
STORET P ETRIEVAL DATE 75/10/23
1 739C1
39 34 50.0 088 ‘.5 20.0
WIL ORN CREEK
17 MOULTRIE CO MAP
1/LAKE SHELBY V ILLE
I•i Y 13 BROG 3.5 MI N OF FINDLAY
1 1EPALES 2111204
4 0000 FEET DEPTH
00630 00625 00610 00671 00665
DATE TIME DEPTH N02&N03 TOT KJEL NH3—N PHOS—DIS PHOS—TOT
FROM OF N-TOTAL N TOTAL ORTHO
TO DAY FEET MG/L MG/L MG/L MG/L P MG/L P
73/06/02 11 00 7.000 0.420 0.068 0.035 0.075
73/07/07 11 4’. 9.300 0.320 0.062 0.033 0.072
73/08/04 11 00 5.400 0.360 0.016 0.048 0.090
73/09/09 10 20 0.470 0.930 0.042 0.048 0.108
73/10/13 16 51 0.490 0.780 0.022 0.042 0.095
73/11/03 11 35 2.400 0.450 0.036 0.023 0.175
73/12/01 10 45 6.600 0.100K 0.012 0.028 0.195
74/01/05 11 30 8.100 0.300 0.016 0.024 0.045
74/02/03 10 00 7.980 0.900 0.230 0.040 0.080
7’./03/02 11 25 7.980 1.600 0.130 0.035 0.095
74/03/16 10 05 8.000 0.500 0.030 0.030 0.100
74/04/06 10 05 7.300 0.500 0.015 0.030 0.065
74/05/04 16 15 8.100 0.300 0.240 0.010 0.025
K VALUE KNOWN TO BE
LESS THAN INDICATED
-------
STORET RETRIEVAL DATE 75/10/23
173901
39 38 00,0 088 42 50.0
W OKAW CREEK
17 MOULTRIE Co MAP
T/LAKE SHELBYVILLE
HWY 121 BROG 1 MI SE OF BETiIANY
1 1EPALES 2111204
4 0000 FEET DEPTH
00630 00625 00610 00671 00665
DATE TIME DEPTH N02&N03 TOT KJEL NH3—N PHOS—DIS PHOS—TOT
FROM OF N-TOTAL N TOTAL ORTHO
TO DAY FEET MG/L MG/L MG/L MG/L P MG/L P
73/06/02 11 50 8.000 0.100K 0.068 0.065 0.110
73/07/07 12 12 8.700 1.540 0.097 0.056 0.110
73/08/04 11 45 4.400 2.100 0.115 0.078 0.105
73/09/09 10 50 1.040 1.590 0.176 0.060 0.165
73/10/13 15 12 2.200 0.780 0.029 0.110 0.220
73/11/03 10 30 2.900 0.650 0.056 0.105 0.315
73/12/01 11 10 5.900 0.100K 0.036 0.048 0.230
74/01/05 13 00 8.200 0.300 0.028 0.036 0.065
74/02/03 10 45 8.200 0.500 0.150 0.055 0.075
74/03/02 11 45 8.500 2.000 0.150 0.040 0.120
74/03/16 10 30 8.300 1.100 0.050 0.040 0.105
74/04/06 10 30 7.700 0.600 0.025 0.030 O.0 5
74/05/04 16 45 9.000 0.300 0.015 0.035 0.052
K VALUE KNOwN TO BE
LESS THAN INDICATED
-------
STORET RETRIEVAL DATE 75/10/23
1739E1
39 37 50.0 088 43 30.0
MARROWBONE CREEK
17 MOULTRIE Co MAP
T/LAKE SHELBYVILLE
SEC RD BR [ )G 1 MI 55€ OF BETHANY
1 1EPALES 2111204
4 0000 FEET DEPTH
00630 00625 00610 00671 00665
DATE TIME DEPTH N02&N03 TOT KJEL. NH3—N PHOS-DIS PHOS-TOT
FROM OF N—IOTAL N TOTAL ORTHO
TO DAY FEET MG/L MG/L MG/L MG/L P MG/L P
73/06/02 11 15 10.500 1.700 0.950 0.180 0.250
73/07/07 12 00 8.100 2.200 0.050 0.037 0.135
73/08/07 09 30 1.000 1.100 0.036 0.042 0.116
73/09/Os 10 37 2.200 3.570 2.200 2.500 2.880
73/10/13 16 38 5.200 2.700 0.58 5 1.030 1.400
73/11/03 11 00 5.300 0.500 0.094 0.240 0.430
73/12/01 11 00 7.300 0.100K 0.016 0.060 0.230
74/01/05 11 45 8.600 0.’.00 0.056 0.064 0.085
74/02/03 10 30 7.980 2.000 0.650 0.060 0.085
74/03/02 11 40 8.600 1.100 0.115 0.035 0.115
74/03/16 10 20 8.500 0.800 0.065 0.060 0.095
74/04/06 10 20 7.680 0.400 0.025 0.040 0.055
74/05/04 16 30 8.500 1.100 0.280 0.085 0.145
K VALUE KNOWN TO 8€
LESS THAN INDICMTED
-------
STORET RETRIEVAL DATE 75/10/23
1739F1
39 34 40.0 088 35 50.0
ASA CREEK
17 MOULTRIE Co MAP
1/LAKE SHELBYVILLE
SEC RD BROG I MI SSE OF SULLIVAN
I1EPALES 2111204
4 0000 FEET DEPTH
00630 00625 00610 00671 00665
DATE TIME DEPTH N02&N03 TOT KJEL NH3-N PHOS—DIS PHOS-TOT
FROM OF N-TOTAL N TOTAL ORTi-lO
TO DAY FEET MG/L MG/L MG/L MG/L P •MG/L P
73/06/02 12 17 10.000 0.960 0.400 0.980 1.200
73/07/07 13 24 9.800 0.520 0.052 1.620 1.650
73/08/04 10 30 7.500 1.500 0.336 0.700 0.770
73/09/08 12 15 8.300 4.300 0.420 6.400 6.850
73/10/13 15 30 5.000 3.500 1.500 2.300 3.000
73/11/03 10 30 5.900 1.150 0.077 2.200 2.600
73/12/01 10 00 7.200 0.900 0.124 0.400 0.635
74/01/04 10 30 8.500 0.900 0.252 0.300 0.470
74/02/02 11 30 8.300 0.400 0.130 0.195 0.250
74/03/02 10 10 8.100 2.100 0.290 0.140 0.250
74/03/16 10 00 8.300 1.300 0.170 0.280 0.380
74/04/06 09 45 7.400 0.850 0.115 0.270 0.340
74/0 /04 18 30 6.900 0.600 0.015 0.035 0.060
-------
STORET RETRIEVAL DATE 75/10/23
1739G1
39 35 20.0 088 33 20.0
JONATHAN RIVER
17 MOULT, IE Co MAP
T/LAKE SHELt3YVILLE
SEC RD GROG 2 MI E oF SULLIVAN
11EPALES 2111204
4 0000 FEET DEPTH
00630 00625 00610 00671 00665
DATE TIME DEPTH N02&N03 TOT KJEL NH3—N PHOS—DIS PHOS-TOT
FROM OF N-TOTAL N TOTAL CJRTHO
TO DAY FELT MG/L MG/L MG/L HG/L P MG/L P
73/06/02 12 32 8.600 0.860 0.100 0.054 0.110
73/07/07 13 40 9.200 1.260 0.120 0.065 0.087
73/08/04 11 15 6.600 2.400 0.110 0.078 0.110
73/09/08 10 15 0.720 2.000 0.510 0.220 0.375
73/10/13 16 30 0.810 1.760 0.290 0.400 0.830
73/11/03 10 45 1.060 1.900 0.250 0.176 0.430
73/1 /01 10 20 6.200 0.100K 0.068 0.096 0.270
74/01/04 10 20 8.600 0.650 0.060 0.035 0.070
74/02/02 11 30 7.980 0.300 0.035 0.050 0.065
74/03/02 10 30 8.200 0.900 0.050 0.040 0.125
74/03/16 10 30 8.400 0.700 0.040 0.045 0.120
74/04/06 10 50 7.600 0.600 0.042 0.040 0.080
74/05/04 17 55 7.000 0.100K 0.020 0.025 0.070
K VALUE KNOWN TO E t
LESS THAN INDICATEL)
-------
STORET RETRIEVAL DATE 75/10/23
1739H1
39 30 40.0 088 32 50.0
WHITLEY CREEK
17 MOULTRIE CO MAP
T/LAKE SHELBYVILLE.
SEC RU BRL)G 2.5 MI S OF ALLENVILLE
L IEPALES 2111204
4 0000 FEET DEPTH
00630 00625 00610 00671 00665
DATE TIME DEPTH N02&N03 TOT KJEL NH3-N PHOS—DIS PHOS—TOT
FROM OF N-TOTAL N TOTAL ORTHO
TO DAY FEET MG/L MG/L MG/L MG/L P MG/L .
73/06/02 09 00 6.300 1.680 0.066 0.048 0.095
73/07/07 14 28 9.900 1.835 0.110 0.048 0.070
73/08/07 11 00 5.900 0.540 0.126 0.065 0.072
73/09/08 09 00 0.380 2.940 0.260 0.100 0.200
73/10/13 13 45 0.066 1.500 0.063 0.085 0.192
73/11/03 09 30 0.130 2.400 0.270 0.138 0.240
73/12/01 09 18 5.300 0.500 0.156 0.072 0.230
74/01/05 09 30 8.800 0.400 0.052 0.028 0.060
74/02/02 10 30 8.600 0.100 0.040 0.045 0.060
74/03/02 09 45 8.200 1.100 0.045 0.045 0.165
74/03/16 09 00 7.700 1.200 0.050 0.055 0.250
74/04/06 08 40 7.000 1.000 0.035 0.055 0.220
74/05/04 19 00 7.600 1.000 0.340 0.990 1.65 )
-------
STORET RETRIEVAL DATE 75/10/23
1739J1
39 28 40.0 088 39 10.0
SAND CREEK
17 SHELBY Co MAP
1/LAKE SHELIJYVILLE
SEC RD BRD(, 3.5 P41 NW OF WINDSOR
1IEPALES 2111204
4 0000 FEET DEPTH
00630 00625 00610 00671 00665
DATE TIME DEPTH NO2t NO3 101 KJEL N113-N PHOS—DIS PHOS-TOT
FROM OF N-TOTAL N TOTAL ORTHO
TO DAY FEET MG/L MG/L MG/I MG/L P MG/L P
73/06/02 09 40 2.600 1.800 0.200 0.029 0.175
73/07/07 15 00 2.900 1.900 0.058 0.015 0.095
73/08/04 09 00 2.200 1.260 0.035 0.011 0.045
73/09/09 09 00 0.750 0.180 0.033
73/10/14 08 10 0.110 1.850 0.490 0.138 0.490
73/11/03 09 30 1.660 2.450 0.440 0.680 1.250
73/12/01 09 30 5.700 0.600 0.112 0.208 0.440
74/01/05 10 07 8.100 0.400 0.072 0.096 0.125
74/02/03 11 30 7.100 1. 00 0.460 0.105 0.140
74/03/02 09 50 7.300 1.400 0.120 0.075 0.180
74/03/16 09 00 7.600 0.700 0.035 0.080 0.180
74/04/06 09 00 6.720 0.800 0.045 0.070 0.125
74/05/04 14 30 6.700 0.400 0.120 0.145 0.170
-------
STORET RETRIEVAL DATE 75/10/23
1739GA TF1739GA
39 39 03.0 088 31 34.0
ILLINOIS MASOI’41C HOME
17 MOULT IE COUNTY
T/LAKE SHELBY V ILLE
JONATHON C EEt(
1 1EPALES
4
P000400
2141204
0000 FEET DEPTH
00630
00625
00610
00671
00665
50051
50053
DATE
TIME
DEPTH
N02&N03
TOT P JEL
NH3-N
PHOS—DIS
PHOS—TOT
FLOW
CONDUIT
FROM
OF
N—TOTAL
N
TOTAL
ORTHO
RATE
FLOW—HGO
TO
DAY
FEET
HG/L
MG/L
HG/L
MG/L P
MG/L P
INST MGI)
MONTHLY
73/08/01
13
30
7.800
1.945
0.110
6.862
7.400
0.049
0.049
73/09/0’.
13
00
13.000
4.400
13.000
0.049
0.049
73/10/05
12
30
14.000
7.800
0.230
11.800
14.000
0.049
0.049
73/11/03
08
30
12.000
4.475
0.440
11.600
12.500
0.049
0.049
73/12/05
07
30
5.800
2.300
0.044
4.300
5.900
0.049
0.049
74/01/07
08
00
13.400
2.900
0.110
9.600
12.500
0.025
0.027
74/02/05
08
00
9.000
4.350
0.710
8.000
13.500
0.049
0.049
74/03/07
08
00
9.100
3.100
0.050K
5.800
6.500
0.049
0.049
74/04/10
20
00
4.900
2.200
0.360
2.800
4.000
0.049
0.049
74/05/11
08
00
16.000
6.300
0.180
11.300
14.000
0.050
0.050
74/06/06
08
00
8.800
5.000
0.310
7.400
8.300
0.050
0.050
Pc VALUE KNOWN TO 8E
LESS 1Hj. N INOICATED
-------
STOWET RETRIEVAL DATE 75/10/23
1739 A AS1739*A P005000
39 33 40.0 088 36 38.0
SULLiVAN STP
17 MOULTRIE COUNTY
1/LAKE SHELBYVILLE
ROBINSON CREEK
I IEPALES 2141204
4 0000 FEET DEPTH
00630
I O2 NO3
N-TOTAL
MG/L
00625
TOT KJEL
N
MG/L
00610
NH3—N
TOTAL
MG/L
00671
PHOS—DIS
ORTHO
HG/L P
00665
PHOS—TOT
MG/L P
50051
FLOW
RATE
INST MGD
50053
CONDUIT
FLOW—MGD
MONTHLY
3.500
1.000
1.200
1.550
1.320
0.800
3.330
4.800
0.010
1.770
5.200
0.609
0.795
19.000
2.600
0.105
4.100
5.225
0.429
0.450
13.000
0.900
0.009
7.900
8.600
0.565
0.477
DATE TIME DEPTH
FROM OF
TO DAY FEET
73/07/24 11 30
73/08/17 09 30
CP(T)—
73/08/17 14 30
73/09/14 13 00
73/10/16 10 30
CP (1) —
73/10/16 13 30
73/11/14 10 00
CP (1) —
73/11/14 13 30
73/12/17 09 30
CP ( T ) —
73/12/17 14 00
74/01/15 09 00
CP(T)—
74/01/15 13 00
74/02/U 08 15
CP (1) —
74/02/11 13 30
74/03/13 08 15
CP(T)—
74/03/13 13 15
74/04/15 14 00
74/05/14 11 30
74/06/13 11 15
CP (1) —
74/06/13 14 30
74/07/15 07 15
CP (1)—
74/07/15 13 30
16.600 1.500 0.120 9.000 9.700 0.426 0.540
10.200 16.000 0.062 6.250 9.000 0.850 0.999
2.880 11.000 1.920 3.400 4.500 0.750 0.616
8.600 3.300 0.120 3.360 4.900 0.875 1.110
4.300
5 • 400
6 • 500
4 • 500
6.000 10.000 5.700 6.500 0.549 0.562
1.500
2 • 500
1.000K
13. 00 0
0.050
0.085
0.050
0.250
1.400
2.300
2 • 650
3.000
1.900
3.600
3.500
3.550
1.320
0.759
0.881
0.80 1
1.120
1.050
0.80 1
0 • 908
K VALUE KNOWN TO d
LESS THAN INDICATED
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STORET RETI1IEVAL DATE 75/10/23
173921 A 5173921 P000010
39 24 35.0 088 46 30.0
DAM EAST ACCESS AREA—SHELBYV ILL(
17139 SHELBY COUNTY
U/LAKE SHEL8YVILLE
LAKE SHELBYVILLE
I 1EPALES 2141204
4 OSlO FEET DEPTH
00630 00625 00610 00671 00665 50051 50053
DATE TIME DEPTH NO2 NO3 TOT KJEL NH3—N PHOS—DIS P 1405—TOT FLOW CONDUIT
FROM OF N—TOTAL N TOTAL ORTHO RATE FLOW—MOO
TO DAY FEET MG/L MG/L MG/I MG/L P MG/L P INST MGD MONTHLY
73/07/27 11 00
CPU)— 14.800 0.150 1.680 2.700 0.002 0.003
73/07/27 16 00
73/08/03 11 00
CP(T)— 27.000 0.006 2.050 2.275 0.002 0.002
73/08/03 16 00
73/09/07 11 00
CP(T)— 0.034 0.185 0.002 0.002
73/09/07 16 00
73/10/05 11 00
CP(T)— 55.000 0.100K 0.010K 0.390 0.530 0.002 0.002
73/10/05 16 00
73/11/06 11 00
- CPU)— 10.400 0.016 0.024 0.190 0.002 0.002
73/11/06 16 00
73/12/07 11 00
CP(T)— 3.500 5.400 0.060 0.040K 0.150 0.002 0.002
73/12/07 16 00
74/01/07 11 00
CP(T)— 0.760 3.000 0.040K 0.170 0.380 0.001 0.001
74/01/07 16 00
74/02/01 11 00
CPU)— 1.200 2.400 0.040K 0.220 1.750 0.001 0.001
74/02/01 16 00
74/03/01 11 00
CP(T)— 1.120 1.600 0.050K 0.050 0.001 0.001
74/03/01 16 00
74/04/03 11 00
CPU)— 3.050 2.300 0.066 0.086 0.050K 0.002 0.001
74/04/03 16 00
74/05/03 11 00
CP(T)— 41.000 1.000K 0.110 0.170 0.240 0.002 0.001
74/05/03 16 00
74/06/04 11 00
CPU)— 4.200 28.000 14.500 0.570 0.650 0.002 0.002
76/06/04 16 00
K VALUE KNOWN TO t3E
LESS THAN IND1C TED
-------
STORET RETRIEVAL DATE 75/10/23
173921 AS173921 P000010
39 24 35.0 088 46 30.0
DAM EAST ACCESS AR A—SHELBYVILLE
11139 SHELBY COUNTY
0/LAKE StItLBYVILLE
LAKE SHELBYV1LLE
11 [ PALES 2141204
4 0000 FEET DEPTH
00630 00625 00610 00671 00665 50051 50053
DATE TiME DEPTH NO2 NO3 TOT KJEL NI-13—N P -iOS—D1S PHOS—TOT FLOW CONDUIT
FROM OF N—TOTAL N TOTAL OWTHO RATE FLOW—MGD
TO DAY FEET M&/L MG/L MG/L MG/L P MG/L P INST M&D MONTHLY
74/07/01 11 00
CP(T)— 30.000 8.500 0.350 1.550 1.800 0.001 0.001
74/07/01 16 00
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