U.S. ENVIRONMENTAL PROTECTION AGENCY
NATIONAL EUTROPHICATION SURVEY
WORKING PAPER SERIES
REPORT
ON
MONROE RESERVOIR
BROWN AND MONR3E COUNTIES
INDIANA
EPA REGION V
WORKING PAPER No, 536
CORVALLIS ENVIRONMENTAL RESEARCH LABORATORY - CORVALLIS, OREGON
and
ENVIRONMENTAL MONITORING & SUPPORT LABORATORY - LAS VEGAS, NEVADA
699-440
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REPORT
ON
I^DNRDE RESERVOIR
BROWN AND MONROE COUNTIES
INDIANA
EPA REGION V
WORKING PAPER No, 336
WITH THE COOPERATION OF THE
INDIANA STATE BOARD OF HEALTH
AND THE
INDIANA NATIONAL GUARD
APRIL, 1976
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CONTENTS
Page
Foreword ii
List of Indiana 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 15
VI. Appendices 16
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11
FOREWORD
The National Eutrophication Survey was initiated in 1972 in
response to an Administration commitment 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 {§303(c)>, water
quality criteria/standards review {§303(c)>, clean lakes {§314(a,b)},
and water quality monitoring {§106 and §305(b)} activities mandated
by the Federal Water Pollution Control Act Amendments of 1972.
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Ill
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, I). S. Environmental Protection Agency)
expresses sincere appreciation to the Indiana State Board of
Health for professional involvement, to the Indiana National
Guard for conducting the tributary sampling phase of the Survey,
and to those Indiana wastewater treatment plant operators who
provided effluent samples and flow data.
The staff of the Division of Water Pollution Control, Indiana
State Board of Health, 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 Alfred F. Ahner, Adjutant General of Indiana,
and Project Officers Lt. Colonel Charles B. Roberts (Retired)
and Colonel Robert L. Sharp, who directed the volunteer efforts
of the Indiana National Guardsmen, are also gratefully acknowledged
for their assistance to the Survey.
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IV
NATIONAL EUTROPHICATION SURVEY
STUDY LAKES
STATE OF INDIANA
LAKE NAME
Bass
Cataract
Crooked
Dallas
Geist
Hamilton
Hovey
James
James
Long
Marsh
Mississinewa
Maxinkuckee
Monroe
Morse
01 in
Oliver
Pi geon
Sylvan
Tippecanoe
Versailles
Wawassee
Webster
Westler
Whitewater
Winona
Witmer
COUNTY
Starke
Owen, Putnam
Steuben
LaGrange
Hamilton, Marion
Steuben
Posey
Kosciusko
Steuben
Steuben
Steuben
Grant, Miami, Wabash
Marshall
Brown, Monroe
Hami 1 ton
LaGrange
LaGrange
Steuben
Noble
Kosciusko
Ripley
Kosciusko
Kosciusko
LaGrange
Union
Kosciusko
LaGrange
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MONROE RESERVOIR
(g Tributary Sampling Site
x Lake Sampling Site
f Sewage Treatment Facility
13 Drainage Area Boundary
',..,? '
39'15
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MONROE RESERVOIR
STORE! NO. 1828
I. CONCLUSIONS
A. Trophic Condition:
Survey data indicate that Monroe Reservoir is eutrophic. Of
the 27 Indiana water bodies sampled in 1973, the reservoir ranked
eighth using a combination of six parameters as an index to over-
all trophic quality*. Eight of the lakes had less and one had the
same median total phosphorus, eight had less median dissolved phos-
phorus and median inorganic nitrogen, seven had less mean chloro-
phyll a_, and 12 had greater mean Secchi disc transparency. Marked
depression or depletion of dissolved oxygen occurred in the hypo-
limnion during periods of thermal stratification.
Survey limnologists noted aquatic macrophytes in the North and
Middle Fork embayments of the reservoir. Allanson et al. (1973)
also reported macrophytes in these embayments.
B. Rate-Limiting Nutrient:
Algal assay results indicate that Monore Reservoir was phos-
phorus limited at the time the assay sample was collected (05/10/73).
The reservoir data indicate phosphorus limitation at all sampling
times.
C. Nutrient Controllability:
1. Point sources—The estimated point-source phosphorus load
amounted to about 21% of the total reaching the reservoir during
the sampling year.
* See Appendix A.
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2
The estimated phosphorus loading during the Survey sampling
year (0.28 g/m2) is just equal to that proposed by Vollenweider
(Vollenweider and Dillon, 1974) as an oligotrophic loading (see
page 14). Although the loading may be in error to some degree
because the phosphorus contributions of a number of small point
sources discharging directly to the lake had to be estimated,
the low phosphorus export rates of all of the tributaries (see
page 14) a're indicative of an overall low phosphorus loading
during the sampling year.
The trophic condition of the reservoir in 1973 probably resulted
from the nutrients contributed by the inundated land as well as
from greater nutrient loadings in the six or so years of existence
of the reservoir prior to the Indiana phosphate detergent ban of
January, 1972, which resulted in an estimated 50% decrease in
domestic wastewater phosphorus. The trophic condition of the
reservoir should improve once a new phosphorus equilibrium is estab-
lished, but this may take some time because the mean hydraulic
retention time of the reservoir is 242 days.
2. Non-point sources—The phosphorus contribution of non-point
sources accounted for about 79% of the total reaching the reservoir
during the sampling year. The gaged tributaries contributed a com-
bined total of 64.7% and ranged from 23.6% (N. Fk., Salt Creek) to
0.3% (Crooked Creek). The ungaged tributaries and immediate drain-
age were estimated to have contributed 8.2% of the total.
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3
As noted above, the phosphorus export rates of the Monroe
Reservoir tributaries were quite low as compared to the rates of
other Indiana tributaries sampled in 1973. The low export rates
would be expected because the drainages are almost entirely forested
and are relatively sparsely-populated.
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4
U. LAKE AND DRAINAGE BASIN CHARACTERISTICS1"
A. Lake Morphometry :
1. Surface area: 43.50 kilometers2.
2. Mean depth: 5.3 meters.
3. Maximum depth: 22.2 meters.
4. Volume: 229.429 x 106 m3.
5. Mean hydraulic retention time: 242 days.
B. Tributary and Outlet:
(See Appendix C for flow data)
1. Tributaries -
Drainage Mean flow
Name area (km2)* (m3/sec)*
South Fk., Salt Creek 265.2 2.52
Middle Fk., Salt Creek 187.0 1.77
Gravel Creek 12.9 0.12
Crooked Creek 9.1 0.08
North Fk., Salt Creek 327.1 3.88
Lower Schooner Creek 31.1 0.29
Brummet Creek 36.0 0.34
Stephens Creek 38.6 0.36
Moore Creek 11.4 0.11
Minor tributaries &
immediate drainage - 157.8 1.49
Totals 1,076.2 10.96
2. Outlet -
Salt Creek 1,119.7** 10.96**
C. Precipitation***:
1. Year of sampling: 114.9 centimeters.
2. Mean annual: 110.5 centimeters.
t Table of metric conversions--Appendix B.
ft McCollam, 1975.
* For limits of accuracy, see Working Paper No. 175, "...Survey Methods,
1973-1976".
** Includes area of lake; outflow adjusted to equal inflow.
*** See Working Paper No. 175.
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5
III. LAKE WATER QUALITY SUMMARY
Monroe 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 a number of depths at six stations on the reservoir (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 phytoplank-
ton 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 and 5 were combined -
station 6 was not sampled in May). Also each time, a depth-integrated
sample was collected from each of the stations for chlorophyll a_
analysis. The maximum depths sampled were 18.6 meters at station
1, 16.5 meters at station 2, 13.7 meters at station 3, 7.9 meters
at station 4, 8.5 meters at station 5, and 5.5 meters at station 6.
The sampling results are presented in full in Appendix D and
are summarized in the following table.
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PARAMETER
TEMP
DISS OXY (MG/L)
CNOCTVY (MCROMO)
PH (STAND UNITS)
TOT ALK (MG/L)
TOT P (MG/L)
ORTHO P (MG/L)
N02»N03 (MG/L)
AMMONIA (MG/L)
KJEL N (MG/L)
INORG N (MG/L)
TOTAL N (MG/L)
CHLRPYL A (UG/L)
SECCHI (METERS)
A. SUMMARY OF PHYSICAL AND
1ST SAMPLING ( 5/10/73)
S SITES
CHEMICAL CHARACTERISTICS FOR
STORET CODE 1826
MONROE RESERVOIR
2ND SAMPLING ( 8/ 6/73)
6 SITES
3RD SAMPLING (10/10/73)
6 SITES
RANGE
11.4
4.3
115.
7.2
12.
0.011
0.002
0.090
0.040
0.200
0.130
0.390
3.2
1.3
- 19.2
9.8
- 153.
8.1
29.
- 0.031
- 0.012
- 0.310
- 0.210
- 0.800
- 0.510
- 0.890
6.6
2.7
MEAN
15.8
7.9
135.
7.6
23.
0.018
0.005
0.240
0.064
0.389
0.304
0.629
4.2
2.2
MEDIAN
16.0
8.8
135.
7.6
23.
0.016
0.004
0.280
0.050
0.400
0.330
0.620
3.5
2.4
RANGE
15.5
0.0
95.
6.6
23.
0.014
0.003
0.040
0.050
0.400
0.100
0.450
6.4
0.4
- 28.6
- 16.2
- 144.
9.0
66.
- 0.072
- 0.023
- 0.270
- 0.980
- 1.700
- 1.120
- 1.840
- 17.2
2.7
MEAN
24.3
3.8
128.
7.3
41.
0.032
0.008
0.101
0.309
0.804
0.410
0.906
10.3
1.3
MEDIAN
25.6
1.6
130.
6.9
35.
0.027
0.006
0.080
0.130
0.600
0.320
0.770
10.3
1.3
RANGE
17.5
0.0
117.
6.6
30.
0.016
0.007
0.020
0.100
0.500
0.130
0.530
3.9
0.6
- 23.7
7.8
- 219.
7.4
95.
- 0.169
- 0.054
- 0.070
- 2.680
- 3.700
- 2.720
- 3.740
8.2
2.7
MEAN
21.3
2.9
141.
7.0
47.
0.056
0.016
0.042
0.693
1.317
0.735
1.359
5.9
1.3
MEDIAN
21.8
2.2
127.
7.0
36.
0.043
0.011
0.040
0.220
0.950
0.260
0.975
5.4
0.9
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B. Biological characteristics:
1. Phytoplankton -
Sampling
Date
05/10/73
08/06/73
10/10/73
2. Chlorophyll a_ -
Sampling
Date
05/10/73
Dominant
Genera
1. Dinobryon sp_.
2. Fragilaria IP_-
3. Cryptomonas sp.
4. Asterionella sp.
5. Flagellates
Other genera
Total
1. Fragilaria sp.
2. Melosira sp.
3. Aphanizomenon sp.
4. Lyngbya sp_.
5. Merismopedia sp.
Other genera
Total
1. Microcystis sp.
2. Melosira sp.
3. Anabaena sp.
4. Flagellates
5. Dactylococcopsis sp.
Other genera
Total
Station
Number
1
2
3
4
5
6
Algal Units
per ml
1
2,162
1,424
976
165
149
99
494
3,307
289
184
145
132
132
538
1,420
Chlorophyll
(ug/D
3.5
3.2
3.2
6.6
4.4
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8
Sampling
Date
08/06/73
10/10/73
Station
Number
1
2
3
4
5
6
1
2
3
4
5
6
Limiting Nutrient Study:
1. Autoclaved, filtered, and nutrient spiked -
a. Stations 1,2, and 3 -
Spike (mg/1)
Ortho P
Cone, (mg/1)
Control
0.050 P
0.050 P + 1.
1.0 N
b. Stations
Spike (mg/1)
Control
0.050 P
0.050 P + 1.
1.0 N
0.005
0.055
0 N 0.055
0.005
4 and 5 -
Ortho P
Cone, (me
0.010
0.060
0 N 0.060
0.010
Inorganic N
Cone, (mg/1)
0.319
0.319
1.319
1.319
Inorganic N
Cone, (mg/1)
0.213
0.213
1.213
1.213
Chlorophyll a_
(yg/1)
17.2
11.4
10.0
10.6
6.4
6.4
7.7
6.2
8.2
3.9
4.6
4.6
Maximum yield
(mg/1-dry wt.)
0.1
8.6
21.9
0.1
Maximum yield
(mg/1-dry wt.)
0.1
4.9
21.1
0.1
Discussion -
The control yields of the assay alga, Selenastrum capri-
cornutum, indicate that the potential primary productivity
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9
of Monroe Reservoir was low at the time the samples were
collected (05/10/73). The results also indicate the reser-
voir was phosphorus limited at that time. Note the lack
of increase in yield with the addition of nitrogen alone;
but with the addition of orthophosphorus, alone or in
combination with nitrogen, the yield increased markedly.
The reservoir data also indicate phosphorus limitation.
The mean inorganic nitrogen to orthophosphorus ratios were
46 to 1 or greater at all sampling times, 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 Indiana 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 months of February and 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 Indiana District Office of the U.S. Geological Survey for the
tributary sites nearest the lake.
In this report, nutrient loads for sampled tributaries were
determined 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 loads, in kg/km2/year, at all stations, except F-l, and
multiplying the means by the ZZ area in km2.
The operators of the Nashville, Ransburg Boy Scout Camp, and Hardin
Ridge Recreation Area wastewater treatment plants provided monthly
effluent samples and corresponding flow data. The operators of the
Fairfax State Recreation Area and the Paynetown Recreation Area
treatment plants provided samples but did not furnish corresponding
* See Working Paper No. 175.
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11
flow data, and the operator of the Hardin Monroe Division did not par-
ticipate; nutrient loads from these sources were estimated at 0.567
kg P and 3.401 kg N/capita/year, and flows were estimated at 0.3785
m3/capita/day. Note that the estimates of phosphorus loads from these
sources and lakeshore septic tanks were reduced by 50% to adjust for
the Indiana phosphate detergent ban instituted in January, 1972.
A. Waste Sources:
1. Known domestic* -
Name
Nashville
Fairfax State
Rec. Area
Hardin Ridge
Rec. Area
Ransburg BSA
Paynetown Rec.
Area
Hardin Monroe
Divn.
Pop.
Served
200
465
282
?
465
200***
Treatment
act. sludge
act. sludge
+ pond
ext. aer. +
P removal
?
act. sludge
?
Mean Flow
(m>/d)
567.8
176.0**
121.1
56.8
176.0**
227.1**
Receiving
Water
N. Fk., Salt
Creek
Monroe Reser-
voir
Monore Reser-
voir
Monroe Reser-
voir
Monroe Reser-
voir
Monroe Reser-
voir
2. Known industrial - None
* Treatment plant questionnaires.
** Design flow; population estimated on basis of flow (0.3785 m3/capita/day)
*** Population adjusted for seasonal use.
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12
B. Annual Total Phosphorus Loading - Average Year:
1. Inputs -
kg P/ % of
Source yr total
a. Tributaries (non-point load) -
South Fk., Salt Creek 2,705 22.6
Middle Fk., Salt Creek 1,450 12.1
Gravel Creek 90 0.8
Crooked Creek 35 0.3
North Fk., Salt Creek 2,830 23.6
Lower Schooner Creek 255 2.1
Brummet Creek 175 1.5
Stephens Creek 165 1.4
Moore Creek 50 0.4
b. Minor tributaries & immediate
drainage (non-point load) - 985 8.2
c. Known domestic STP's -
Nashville 1,810 15.1
Fairfax Rec. Area 265 2.2
Hardin Ridge Rec. Area 5 <0.1
Ransburg BSA 10 0.1
Paynestown Rec. Area 265 2.2
Hardin Monroe Divn. 115 1.0
d. Septic tanks* - 20 0.2
e. Known industrial - None
f. Direct precipitation** - 760 6.2
Total 11,990 100.0
2. Outputs -
Lake outlet - Salt Creek 6,695
3. Net annual P accumulation - 5,295 kg.
* Estimate based on 135 lakeshore dwellings; see Working Paper No. 175.
** See Working Paper No. 175.
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13
Annual Total Nitrogen Loading - Average Year:
1. Inputs -
kg N/ % of
Source yr total
a. Tributaries (non-point load) -
South Fk.t Salt Creek 78,070 20.0
Middle Fk., Salt Creek 53,915 13.8
Gravel Creek 2,855 0.7
Crooked Creek 2,435 0.6
North Fk., Salt Creek 109,440 28.0
Lower Schooner Creek 10,260 2.6
Brummet Creek 8,560 2.2
Stephens Creek 18,450 4.7
Moore Creek 2,750 0.7
b. Minor tributaries & immediate
drainage (non-point load) - 46,510 11.9
c. Known domestic STP's -
Nashville 5,340 1.4
Fairfax Rec. Area 1,580 0.4
Hardin Ridge Rec. Area 125 <0.1
Ransburg BSA 115 <0.1
Paynetown Rec. Area 1,580 0.4
Hardin Monroe Divn. 680 0.2
d. Septic tanks* - 1,440 0.4
e. Known industrial - None
f. Direct precipitation** - 46,975 12.0
Total 391,080 100.0
2. Outputs -
Lake outlet - Salt Creek 386,755
3. Net annual N accumulation - 4,325 kg.
* Estimate based on 135 lakeshore dwellings; see Working Paper No. 175.
** See Working Paper No. 175.
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14
D. Mean Annual Non-point Nutrient Export by Subdrainage Area:
Tributary kg P/kmVyr kg N/km2/yr
South Fk.5 Salt Creek 10 294
Middle Fk., Salt Creek 8 288
Gravel Creek 7 221
Crooked Creek 4 268
North Fk., Salt Creek 9 335
Lower Schooner Creek 8 330
Brummet Creek 5 238
Stephens Creek 4 478
Moore Creek 4 241
E. Yearly Loads:
In the following table, the existing phosphorus loadings
are compared to those proposed by Vollenweider (Vollenweider
and Dillon, 1974). Essentially, his "dangerous" loading is
one at which the receiving water would become eutrophic or
remain eutrophic; his "permissible" loading is that which
would result in the receiving water remaining oligotrophic
or becoming oligotrophic if morphometry permitted. A meso-
trophic loading 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/mVyr 0.28 0.12 9.0 0.1
Vollenweider phosphorus loadings
(g/m2/yr) based on mean depth and mean
hydraulic retention time of Monroe Reservoir:
"Dangerous" (eutrophic loading) 0.56
"Permissible" (oligotrophic loading) 0.28
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15
V. LITERATURE REVIEWED
Allanson, Brian R., Charles J. Zimmerman, and Diane K. Smith, 1973.
A report on the limnology of Monroe Reservoir. Occas. Pap. No.
1, Sch. Publ. & Environ. Affairs, IN U., Bloomington.
McCollam, Archie, 1975. Personal communication (lake morphometry).
U.S. Geol. Surv., Indianapolis.
Vollenweider, R. A., and P. J. Dillon, 1974. The application of
the phosphorus loading concept to eutrophication research.
Natl. Res. Council 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
CODE
1805
1811
1817
1827
182H
1829
1836
1837
1839
1840
1841
1842
1843
1844
1845
1846
1847
1848
1849
1850
1851
.852
1853
1854
1R55
1856
1857
LAKE NAME
CATARACT LAKE
GEIST RESERVOIR
JAMES LAKE
MISS1SSINEWA RESERVOIR
MONROE RESERVOIR
MORSE RESERVOIR
WAWASEE LAKE
WE8STER LAKE
WHITEWATER LAKE
WINONA LAKE
WESTLER LAKE
EITHER LAKE
LAKE MAAINKUCKEE
TIPPECANOE LAKE
DALLAS LAKE
OLIN LAKE
OLIVER LAKE
SYLVAN LAKE
HOVEY LAKE
VERSAILLES LAKE
BASS LAKE
CROOKED LAKE
LAKE JAMES
LONG LAKE
PIGEON LAKE
MARSH LAKE
HAMILTON LAKE
MEDIAN
TOTAL P
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
.058
.074
.024
.107
.025
.084
.012
.025
.084
.035
.035
.035
.020
.019
.029
.012
.009
.170
.062
.139
.040
.019
.016
.204
.058
.093
.033
MEDIAN
INORG N
1.660
1.080
1.030
2.400
0.325
3.325
0.210
0.790
1.620
1.250
0.860
0.900
0.220
0.195
0.830
1.460
0.920
0.130
1.050
1.090
0.250
0.120
0.190
1.920
1.945
0.270
0.720
500-
MEAN SEC
466.
472.
434.
473.
438.
473.
364.
431.
470.
444.
427.
440.
400.
391.
413.
403.
392.
469.
489.
482.
471.
410.
352.
442.
442.
451.
413.
667
500
000
444
B23
222
500
000
167
667
125
333
400
500
333
333
000
833
333
000
375
111
444
667
t>67
333
167
MEAN
CHLORA
10
45
11
15
6
56
5
11
33
11
10
11
5
6
10
4
3
47
84
25
29
5
4
16
11
34
17
.744
.950
.533
.778
.947
.167
.000
.500
.083
.211
.712
.917
.483
.050
.067
.867
.767
.480
.267
.078
.367
.578
.856
.100
.900
.467
.450
15-
MIN 00
15.
11.
15.
15.
15.
15.
14.
15.
15.
15.
15.
15.
15.
15.
15.
14.
14.
14.
7.
14.
7.
15.
15.
15.
15.
15.
15.
000
600
000
000
000
000
600
ooo
000
000
000
000
000
000
000
900
800
800
600
500
000
000
000
000
000
000
000
MEDIAN
DISS ORTnO
o.ou
0.009
0.008
0.029
o.oo'
0.009
O.OOJ
0.005
0.012
0.011
0.013
0.011
0.003
0.005
0.014
0.003
0.004
0.017
0.024
0.019
0.012
0.005
0.005
0.150
0.015
0.055
0.018
-------
PERCENT OF LAKES WITri HIGHER VALUES (NUMBER OF LAKES WITH HIGHEw VALUES)
LAKE
CODE
1805
1811
1817
1837
1828
1829
1836
1837
1839
1840
1841
1842
18*3
1844
1845
18<>6
1847
1648
1849
1850
1851
1852
1853
1854
1855
1856
1857
LAKE NAME
CATARACT LAKE
GEIST RESERVOIR
JAMES LAKE
MISSISSINE«/A RESERVOIR
MONROE RESERVOIR
MORSE RESERVOIR
WAWASEE LAKE
WEBSTEP LAKE
WHITEWATER LAKE
WINONA LAKE
WESTLER LAKE
WITHER LAKE
LAKE MAXINKUCKEE
TIPPECANOE LAKE
DALLAS LAKE
OLIN LAKE
OLIVER LAKE
SYLVAN LAKE
HOVEY LAKE
VERSAILLES LAKE
BASS LAKE
CROOKED LAKE
LAKE JAMES
LONG LAKE
PIGEON LAKE
MARSH LAKE
HAMILTON LAKE
MEDIAN
TOTAL P
37
27
73
12
67
23
94
67
19
50
50
50
77
85
62
94
100
4
31
8
42
81
aa
0
37
15
58
I 9)
( 71
( 191
< 3)
( 17)
( 6)
( 24)
( 17)
( 5)
< 12)
( 12)
( 12)
I 20)
( 22)
( 16)
( 24)
( 26)
( 1)
1 8)
< 2)
( 11)
( 21)
( 23)
( 0)
( 9)
( 4)
( 15)
MEDIAN
IMO«G N
15
35
42
4
b9
0
85
62
19
27
54
50
81
aa
58
23
46
96
38
31
77
100
92
12
8
73
65
I 4)
< 9)
< 11)
< 1)
I 18)
I 0)
( 22)
( 16)
( 51
( 7)
( 14)
( 131
( 21)
( 23)
( 15)
( 6)
( 12)
< 25)
( 10)
( 8)
( 20)
( 26)
( 24)
( 3)
( 2)
< 19)
( 17)
500-
MEAN SEC
31
15
S8
8
54
12
96
62
23
38
65
50
85
92
69
81
aa
27
0
4
19
77
100
44
44
35
73
( a)
( 4)
( IS)
( 2)
( 14)
< 3)
< 25)
( 16)
( 6)
( 10)
< 17)
( 13)
( 22)
( 24)
( 18)
( 21)
I 23)
( 7)
( 0)
( 1)
( 5)
( 20)
( 26)
I 11)
< 11)
( 9)
< 19)
MEAN
CHLORA
62
12
50
38
/3
4
88
54
19
SB
65
42
85
77
69
92
100
8
0
27
23
81
96
35
46
15
31
I 16)
( 3)
1 13)
( 10)
( 19)
( 1)
1 23)
I 14)
I 5)
( 15)
( 17)
< ID
( 22)
I 20)
( 18)
I 24)
( 26)
I 2)
( 0)
( 7)
( 6)
( 21)
( 25)
( 9)
( 12)
( 4)
( 8)
Ib-
MIN 00
35
92
35
35
35
35
85
35
35
35
35
35
35
35
35
73
79
79
96
88
too
35
35
35
35
35
35
I 0)
( 24)
( 0)
( 0)
( 0)
( 0)
( 22)
( 0)
( 0)
( 0)
( 0)
( 0)
( 0)
( 0)
I 0)
( 19)
( 20)
( 20)
( 25)
( 23)
I 26)
( 0)
( 0)
I 0)
( 0)
I 0)
( 0)
MEDIAN
DISS ORTHO P
37
62
65
a
69
58
98
81
42
52
37
52
98
85
31
92
88
23
12
15
46
75
75
0
27
4
19
( 9)
( 16)
( 17)
( 2)
( 18)
( 15)
( 25)
( 21)
( 11)
( 13)
( 9)
( 13)
( 25)
< 22)
( 8)
( 24)
( 23)
( 6)
( 3)
( 4)
( 12)
( 19)
( 19)
( 0)
( 7)
< 1)
( 5)
INtlEX
NO
217
243
323
105
367
132
546
361
157
260
306
279
461
462
324
455
501
237
177
173
307
449
486
126
Hf
177
281
-------
LAKES RANKED BY INDEX NOS.
RANK LAKE CODE LAKE NAME INDEX NO
1 1836 WAWASEE LAKE 546
2 18*7 OLIVER LAKE 501
3 1853 LAKE JAMES 486
4 1844 TIPPECANOE LAKE 462
5 1B43 LAKE MAXINKUCKEE 461
6 1846 OLIN LAKE 455
7 1852 CROOKED LAKE 449
8 1828 MONROE RESERVOIR 367
9 1837 WEBSTER LAKE 361
10 1845 DALLAS LAKE 324
11 1817 JAMES LAKE 323
12 1851 BASS LAKE 307
13 1841 WESTLER LAKE 306
14 1857 HAMILTON LAKE 281
15 1842 WITMER LAKE 279
16 1840 WINONA LAKE 260
17 1811 6EIST RESERVOIR 243
18 1848 SYLVAN LAKE 237
19 1805 CATARACT LAKE 217
20 1855 PIGEON LAKE 197
21 1856 MARSH LAKE 177
22 1849 HOVE* LAKE 177
23 1850 VERSAILLES LAKE 173
24 1839 WHITEWATER LAKE 157
25 1829 MORSE RESERVOIR 132
26 1854 LONG LAKE 126
27 1827 MISSISSINEWA RESERVOIR 105
-------
APPENDIX B
CONVERSION FACTORS
-------
CONVERSION FACTORS
Hectares x 2.471 = acres
Kilometers x 0.6214 = miles
Meters x 3.281 = feet
-4
Cubic meters x 8.107 x 10 = acre/feet
Square kilometers 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 = Ibs/square mile
-------
APPENDIX C
TRIBUTARY FLOW DATA
-------
TRIBUTARY FLOW INFORMATION FOR INDIANA
03/39/76
LAKE CODE 1828
MONROE RESERVOIR
TOTAL DRAINAGE AREA OF LAKE(SO KM) 1119.7
SUB-DRAINAGE
TRIBUTARY AREA(SO KM)
JAN
FEB
MAR
APR
MAY
NORMALIZED FLOWS(CMS)
JUN JUL ALtG
SEP
OCT
NOV
DEC
MEAN
1828A1
1828B1
1828C1
1828D1
1828E1
1828F1
1828G1
1828H1
1828J1
1828K1
1828ZZ
1119.9
265.2
187.0
12.9
9.1
327.1
31.1
36.0
38.6
11.4
157.7
14.33
3.40
2.37
0.147
0.102
7.25
0.365
0.428
0.459
0.130
1.99
26.53
3.85
2.71
0.184
0.127
6.43
0.445
0.515
0.552
0.161
2.28
29.45
5.30
3.77
0.269
0.190
8.07
0.637
0.736
0.790
0.238
3.17
21.75
5.04
3.57
0.246
0.173
7.96
0.595
0.688
0.736
0.218
3.00
30.58
3.31
2.32
0.159
0.110
6.57
0.382
0.442
0.473
0.139
1.96
16.20
2.47
1.74
0.122
0.085
2.63
0.292
0.337
0.362
0.108
1.47
6.65
1.53
1.07
0.071
0.051
1.46
0.176
0.204
0.218
0.062
0.90
3.68
0.63
0.43
0.022
0.014
0.34
0.057
0.068
0.074
0.019
0.35
1.39
0.56
0.38
0.022
0.015
0.32
0.057
0.065
0.071
0.019
0.32
2.10
0.62
0.42
0.022
0.015
0.35
0.059
0.068
0.074
0.020
0.35
3.23
1.31
0.92
0.062
0.045
1.36
0.153
0.176
0.190
0.057
0.78
12.29
2.3,2
1.65
0.122
0.085
3.96
0.283
0.328
0.351
0.108
1.39
13.95
2.52
1.77
0.120
0.084
3.88
0.291
0.337
0.361
0.106
1.49
SUMMARY
TOTAL DRAINAGE AREA OF LAKE =
SUM OF SUB-DRAINAGE AREAS =
1119.7
1076.1
TOTAL FLOW IN
TOTAL FLOW OUT
131.99
168.18
MEAN MONTHLY FLOWS AND DAILY FLOWS(CMS)
TRIBUTARY MONTH YEAR.
1828A1
MEAN FLOW DAY
FLOW DAY
FLOW DAY
FLOW
183881
6
7
8
9
10
11
12
2
3
4
5
6
7
a
9
10
11
12
1
2
3
it
5
73
73
73
73
73
73
73
74
74
74
74
73
73
73
73
73
73
73
74
74
74
74
74
38.879
15.744
2.713
1.422
1.390
1.393
4.417
37.010
32.791
32.026
11.667
4.248
3.511
0.510
0.110
0.102
1.557
4.502
7.362
3.936
7.362
7.249
6.060
9
11
14
5
4
8
18
9
9
6
5
9
11
14
5
4
8
18
16
9
9
6
5
6.116
.869
.444
.444
.388
.388
.444
52.669 24
29.733 23
5.720
20.728
2.265
0.963
1.642
0.079
0.057
0.068
0.595
5.862
4.248 24
3.256 23
3.511
2.435
20.841
52.952
5.862
4.870
-------
TRIBUTARY FLOW INFORMATION FOR INDIANA
03/29/76
LAKE CODE 1828
MONROE RESERVOIR
MEAN MONTHLY FLOWS AND DAILY FLOWS(CMS)
TRIBUTARY MONTH YEAR
182BC1
182BD1
1828E1
1828F1
6
7
8
9
10
11
12
1
2
3
4
5
6
7
8
9
10
11
12
1
2
3
4
5
6
7
8
9
10
11
12
1
2
3
4
5
6
7
8
9
10
11
12
1
2
3
4
5
73
73
73
73
73
73
73
74
74
74
74
74
73
73
73
73
73
73
73
74
74
74
74
74
73
73
73
73
73
73
73
74
74
74
74
74
73
73
73
73
73
73
73
74
74
74
74
74
MEAN FLOW DAY
2.945
2.407
0.340
0.079
0.071
1.133
2.945
5.040
2.775
4.984
4.927
5.352
0.207
0.170
0.025
0.006
0.006
0.079
0.215
0.368
0.195
0.340
0.311
0.396
0.147
0.119
0.011
0.002
0.015
0.057
0.221
0.249
0.136
0.246
0.241
0.269
5.125
4.163
0.595
0.136
0.122
U897
5.239
8.637
4.814
8.580
8.495
9.288
9
11
14
5
4
8
18
16
9
9
6
5
9
11
14
5
4
8
18
16
9
9
6
5
9
11
14
5
4
8
IB
16
9
9
6
5
9
11
14
5
4
8
18
16
9
9
6
5
FLOW DAY
FLOW DAY
FLOW
2.379
0.708
1.133
0.054
0.031
0.048
0.425
4.134
2.718
2.350
2.407
1.699
0.096
0.048
0.082
0.003
0.002
0.003
0.028
0.283
0.201
0.156
0.173
0.125
0.091
0.025
0.051
0.001
0.001
0.001
0.014
0.198
0.139
0.110
0.119
0.082
3.285
1.161
1.982
0.096
0.054
0.082
0.736
7.023
4.984
3.908
4.134
2.917
24
23
24
23
24
23
24
23
4.078
3.426
0.283
0.207
0.198
0.159
60 994
5.805
-------
TRIBUTARY FLOW INFORMATION FOR INDIANA
03/29/76
LAKE CODE 1828
MONROE RESERVOIR
MEAN MONTHLY FLOWS AND DAILY FLOWS
TRIBUTARY MONTH YEAR MEAN FLOW DAY
182861
1828H1
1828J1
1828K1
6
7
6
9
10
11
12
1
2
3
4
5
6
7
8
9
10
11
12
1
2
3
4
5
6
7
8
9
10
11
12
1
2
3
4
5
6
7
a
9
10
11
12
1
2
3
4
5
73
73
73
73
73
73
73
74
74
74
74
74
73
73
73
73
73
73
73
74
74
74
74
74
73
73
73
73
73
73
73
74
74
74
74
74
73
73
73
73
73
73
73
74
74
74
74
74
FLOW DAY
FLOW DAY
FLOW
0.283
0.102
0.003
0.001
0.000
0.008
0.510
0.793
0.538
0.991
0.680
1.019
0.595
0.481
0.065
0.001
0.008
0.212
0.595
1.019
O.S66
1.019
0.934
1.104
0.3S7
0.125
0.014
0.002
0.000
0.252
0.651
0.991
0.680
1.218
0.906
1.246
0.110
0.040
0.006
0.001
0.000
0.065
0.193
0.283
0,204
0.368
0.269
0.368
9
11
14
5
4
8
18
16
9
9
6
5
9
11
14
5
4
8
ia
16
9
9
6
5
9
11
14
5
4
a
18
16
9
9
6
5
9
11
14
5
4
8
18
16
9
9
6
5
0.204
0.011
0.011
0.001
0.000
0.000
0.059
0.623
0.566
0.510
0.396
0.261
0.227
0.133
0.227
0.001
0.001
0.003
0.008
0.934
0.566
0.453
0.481
0.340
0.396
0.025
0.025
0.002
0.000
0.001
0.076
0.821
0.736
0.623
0.510
0.340
0.119
0.008
0.008
0.001
0.000
o.ooo
0.023
0.244
0.221
0.187
0.150
0.099
24
23
24
23
24
23
24
23
0.821
0.680
0.821
0.765
1.048
0.850
0.311
0.255
-------
TRIBUTARY FLOW INFORMATION FOR INDIANA
03/29/76
LAKE CODE 1828
MONROE RESERVOIR
MEAN MONTHLY FLOWS ANO DAILY FLOWS(CMS)
TRIBUTARY
1828ZZ
MONTH YEAR
6
7
8
9
10
11
12
1
2
3
4
5
73
73
73
73
73
73
73
74
74
74
74
74
MEAN FLOW DAY
2.560
2.112
0.306
0.068
0.062
0.943
2.582
4.417
2.379
4.389
4.304
4.757
9
11
14
5
4
8
18
16
9
9
6
5
FLOW DAY
1.642
0.595
0.991
0.048
0.028
0.040
0.368
3.568
2.492 24
1.954 23
2.095
1.472
FLOW DAY
FLOW
3.568
2.945
-------
APPENDIX D
PHYSICAL and CHEMICAL DATA
-------
STORET RETRIEVAL DATE 76/03/30
182601
39 00 31.0 086 30 57.0 3
MONROE RESERVOIR
18105 INDIANA
051891
DATE
FROM
TO
73/05/10
73/08/06
TIME
OF
DAY
10 20
10 20
10 20
10 20
10 20
10 20
10 20
16 OS
16 05
16 05
DEPTH
FEET
0000
0006
0015
0025
0040
0050
0061
0000
0005
0015
16 05 0025
73/10/10
DATE
FROM
TO
73/05/10
73/08/06
73/10/10
16 05
16 05
13 40
13 40
13 40
13 40
13 40
13 40
TIME
OF
DAY
10 20
10 20
10 20
10 20
10 20
10 20
10 20
16 05
16 05
16 05
16 05
16 05
16 05
13 40
13 40
13 40
13 40
13 40
13 40
0035
0048
0000
0005
0015
0025
0035
0046
DEPTH
FEET
0000
0006
0015
0025
0040
0050
0061
0000
0005
0015
0025
0035
0048
0000
0005
0015
0025
003b
0046
00010
WATER
TEMP
CENT
15.8
15.7
15.1
15.0
13.9
12.7
11.4
28.4
27.1
26.6
21.6
17.4
15.5
23.7
23.2
22.6
21.9
18.7
17.5
00665
PHOS-TOT
MG/L P
0.011
0.013
0.014
0.020
0.016
0.019
0.022
0.014
0.023
0.016
0.018
0.027
0.036
0.016
0.021
0.019
0.031
0.092
0.169
00300
00
MG/L
9.5
9.8
a. 8
7.8
4.6
4.3
8.2
16.2
0.2
0.0
0.2
7.0
4.6
0.1
0.0
0.0
32217
CHLRPHYL
A
UG/L
3.5
17.2
7.7
00077 00094
TRANSP CNDUCTVY
SECCMI FIELD
INCHES MICROMHO
108 140
140
140
140
140
150
153
80 130
126
125
134
136
132
108 128
124
124
157
195
219
11EPALES 2111202
0065 FEET DEPTH CLASS 00
00400 00410 00610 00625
PH
SU
7.60
7.60
7.60
7.60
7.50
7.30
7.20
8.30
7.90
6.70
6.80
6.80
6.80
7.40
7.10
7.00
7.00
6.90
6.90
T ALK
CAC03
MG/L
23
22
24
24
27
26
29
35
33
35
49
63
66
39
36
37
62
93
92
NH3-N
TOTAL
MG/L
0.040
0.040
0.040
0.050
0.080
0.120
0.210
0.100
0.060
0.090
0.370
0.840
0.980
0.180
0.120
0.150
0.770
2.100
2.440
TOT KJEL
N
MG/L
0.400
0.400
0.200
0.200
0.200K
0.300
0.300
0.700
0.600
0.600
0.800
1.500
1.700
1.000
0.600
0.600
0.900
2.700
3.200
00630
N02&N03
N-TOTAL
MG/L
0.310
0.300
0.290
0.290
0.290
0.280
0.300
0.070
0.060
0.060
O.OSO
0.100
0.140
0.060
0.060
0.070
0.030
0.050
0.050
00671
PMOS-DIS
ORTMO
MG/L P
0.006
0.005
0.007
0.007
0.004
0.004
0.006
0.007
0.006
0.005
0.005
0.010
0.012
0.012
0.013
0.011
0.011
0.023
0.031
K VALUE KNOWN TO BE
LESS THAN INDICATEO
-------
STORET RETRIEVAL DATE 76/03/30
183802
39 01 26.0 086 27 54.0 3
MONROE RESERVOIR
18105 INDIANA
051891
11EPALES
2111202
0058 FEET DEPTH CLASS
DATE
FROM
TO
73/05/10
73/08/06
73/10/10
DATE
FROM
TO
73/05/10
73/08/06
73/10/10
TIME DEPTH
OF
DAY FEET
10 45 0000
10 45 0006
10 45 0015
10 45 0025
10 45 0040
10 45 0054
15 35 0000
15 35 0005
15 35 0015
15 35 0025
15 35 0041
13 15 0000
13 15 0005
13 15 0015
13 15 0025
13 15 0035
13 15 0040
TIME DEPTH
OF
DAY FEET
10 45 0000
10 45 0006
10 45 0015
10 45 0025
10 45 0040
10 45 0054
15 35 0000
15 35 0005
15 35 0015
15 35 0025
15 35 0041
13 15 0000
13 15 0005
13 15 0015
13 15 0025
13 15 0035
13 15 0040
00010
WATER
TEMP
CENT
16.4
16.4
16.3
16.0
14.8
12.2
28.6
28.5
26.5
21.9
16.8
23.2
22.5
22.4
21.9
18.8
18.2
00665
PHOS-TOT
M6/L P
0.012
0.013
0.029
0.013
0.013
0.015
0.021
0.016
0.017
0.028
0.028
0.029
0.025
0.026
0.051
0.104
0.132
00300
DO
MG/L
9.6
9.6
9.5
8.4
4.5
8.8
7.2
0.2
0.4
6.0
5.6
1.6
0.0
0.1
32217
CHLRPHYL
A
UG/L
3.2
11.4
6.2
00077 00094
TRANSP CNDUCTVY
SECCHI FIELD
INCHES MICROMHO
108 140
135
135
135
135
145
105 130
130
122
144
135
70 127
125
124
144
184
188
00400
PH
SU
7.60
7.60
7.60
7.60
7.60
7.50
8.90
8.40
7.10
6.90
6.90
7.10
7.00
6.90
6.80
7.00
7.00
00410
T ALK
CAC03
MG/L
21
22
24
24
22
26
33
.32
34
62
62
30
30
30
48
86
95
00610
NH3-N
TOTAL
MG/L
0.050
0.040
0.040
0.040
0.060
0.120
0.060
0.060
0.050
0.650
0.910
0.100
0.130
0.170
0.650
2.090
2.380
00
00625
TOT KJEL
N
MG/L
0.400
0.300
0.300
0.300
0.300
0.400
0.500
0.400
0.400
1.200
1.600
0.800
0.500
0.600
1.000
2.800
3.600
00630
N02&N03
N-TOTAL
MG/L
0.300
0.300
0.300
0.290
0.290
0.280
0.040
0.060
0.050
0.120
0.110
0.030
0.040
0.040
0.020
0.040
0.040
00671
* PHOS-DIS
ORTHO
MG/L P
0.005
0.004
0.003
0.004
0.008
0.005
0.003
0.004
0.003
0.006
0.017
0.011
0.011
0.011
0.013
0.041
0.054
-------
STORET RETRIEVAL DATE 76/03/30
182803
39 04 02.0 086 26 22.0 3
MONROE RESERVOIR
18105 INDIANA
051891
11EPALES 2111202
0050 FEET DEPTH CLASS 00
DATE
FROM
TO
73/05/10
73/08/06
73/10/10
DATE
FROM
TO
73/05/10
73/08/06
73/10/10
TIME DEPTH
OF
DAY FEET
12 50 0000
12 50 0006
12 50 0015
12 50 0024
12 50 0032
12 50 0045
15 10 0000
15 10 0005
15 10 0015
15 10 0025
15 10 0034
12 45 0000
12 45 0005
12 45 0015
12 45 0025
12 45 0035
TIME DEPTH
OF
DAY FEET
12 50 0000
12 50 0006
12 50 0015
12 50 0024
12 50 0032
12 50 0045
15 10 0000
15 10 0005
15 10 0015
15 10 0025
15 10 0034
12 45 0000
12 45 0005
12 45 0015
12 45 0025
12 45 0035
00010
WATER
TEMP
CENT
16.6
16.6
16.5
16.3
16.0
15.2
28.5
27.6
25.6
22.3
18.0
23.1
22.6
22.5
21.8
19.2
00665
PHOS-TOT
MG/L P
0.015
0.014
0.015
0.015
0.014
0.018
0.024
0.019
0.029
0.034
0.027
0.030
0.025
0.035
0.043
0.121
00300
DO
MG/L
8.8
9.4
9.3
8.9
8.4
9.6
3.4
0.2
0.0
7.8
5.0
0.2
0.0
32217
CHLRPHYL
A
UG/L
3.2
10.0
8.2
00077 00094
TRANSP CNDUCTVY
SECCHI FIELD
INCHES MICROMHO
96 140
140
140
140
135
135
72 126
124
120
124
141
42 125
125
127
135
189
00400
PH
SU
7.
7.
7.
7.
7.
7.
8.
8.
6.
6.
6.
7.
7.
7.
6.
7.
60
70
70
70
70
60
90
20
60
90
90
40
30
10
80
00
00410
T ALK
CAC03
MG/L
23
21
24
23
23
22
31
28
36
42
60
36
36
33
39
82
00610
NH3-N
• TOTAL
MG/L
0.040
0.040
0.050
0.050
0.060
0.060
0.080
0.060
0.200
0.550
0.830
0.120
0.110
0.170
0.550
2.680
00625
TOT KJEL
N
MG/L
0.600
0.400
0.400
0.400
0.300
0.300
0.500
0.400
0.500
1.100
1.400
0.600
0.500
0.800
1.100
3.700
00630
N02&N03
N-TOTAL
MG/L
0.280
0.280
0.290
0.280
0.280
0.270
0.080
0.070
0.120
0.100
0.070
0.030
0.030
0.040
0.030
0.040
. 00671
PHOS-DIS
ORTHO
MG/L P
0.006
0.012
0.004
0.006
0.008
0.005
0.005
0.005
0.009
0.007
0.005
Ooooa
0.010
0.012
0.010
0.032
-------
STORET RETRIEVAL DATE 76/03/30
182804
39 06 02.0 086 24 28.0 3
MONROE RESERVOIR
18105 INDIANA
051891
DATE
FROM
TO
73/05/10
73/08/06
73/10/10
DATE
FROM
TO
73/05/10
73/08/06
73/10/10
TIME DEPTH
OF
DAY FEET
13 35 0000
13 35 0006
13 35 0015
13 35 0026
14 45 0000
14 45 0005
14 45 0010
14 45 0018
12 20 0000
12 20 0005
12 20 0010
12 20 0018
TIME DEPTH
OF
DAY FEET
13 35 0000
13 35 0006
13 35 0015
13 35 0026
14 45 0000
14 45 0005
14 45 0010
14 45 0018
12 20 0000
12 20 0005
12 20 0010
12 20 0018
00010
WATER
TEMP
CENT
18.7
18.5
16.9
15.9
27.7
26.1
25.3
23.9
22.3
21.2
20.9
20.5
00665
PHOS-TOT
MG/L P
0.018
0.024
0.020
0.021
0.025
0.045
0.072
0.051
0.051
0.035
0.043
0.067
00300
DO
MG/L
9.
7.
6.
7.
2.
0.
4.
4.
2.
32217
00077 00094
TRANSP CNDUCTVY
SECCHI FIELD
INCHES MICROMHO
3
7
8
0
2
6
8
0
2
60 125
125
125
130
31 139
136
138
144
24 120
119
117
118
11EPALES 2111202
0030 FEET DEPTH CLASS 00
00400 00410 00610 00625 00630 00671
PH T ALK NH3-N TOT KJEL N02&N03 PHOS-OIS
CAC03 TOTAL N N-TOTAL ORTHO
su
7.60
7.60
7.60
7.50
9.00
7.00
6.70
6.60
7.10
6.80
6.70
6.60
MG/L
23
12
27
26
35
39
41
42
30
30
31
33
MG/L
0.040
0.040
0.050
0.070
0.060
0.080
0.090
0.190
0.160
0.220
0.220
0.340
MG/L
0.500
0.500
0.500
0.500
0.500
0.400
0.400
0.700
1.100
0.800
0.700
0.700
MG/L
0.120
0.140
0.120
0.150
0,050
0.080
0.090
0.140
0.040
0.040
0.040
0.050
MG/L P
0.003
0.004
0.004
0.004
0.007
0.006
0.006
0.005
0.007
0.007
0.008
0.011
CHLRPHYL
A
UG/L
6.
10.
3.
6
6
9
-------
STORE! RETRIEVAL DATE 76/03/30
DATE
FROM
TO
73/05/10
73/08/06
73/10/10
DATE
FROM
TO
73/05/10
73/08/06
73/10/10
TIME DEPTH
OF
DAY FEET
14 00 0000
14 00 0006
14 00 0015
14 00 0028
14 25 0000
12 00 0000
TIME DEPTH
OF
DAY FEET
14 00 0000
14 00 0006
14 00 0015
14 00 0028
14 25 0000
12 00 0000
00010
WATER
TEMP
CENT
19.2
18.3
15.7
15.1
00665
PHOS-TOT
MG/L P
0.021
0.031
0.021
0.025
00300
DO
MG/L
9.1
4.7
4.9
32217
CHLRPHYL
A
UG/L
4.4
6.4
4.6
00077
TRANSP CK
SECCHI FIELD
INCHES Ml
52
14
28
182805
39 04 38.0 086 19 34.0 3
MONROE RESERVOIR
18013 INDIANA
051891
11EPALES 2111202
0032 FEET DEPTH CLASS 00
94
TVY
MHO
120
115
125
125
00400
PH
SU
8.10
7.90
7.50
7.40
00410
T AUK
CAC03
MG/L
21
19
23
19
00610
NH3-N
TOTAL
MG/L
0.040
0.050
0.120
0.100
00625
TOT KJEL
N
MG/L
0.300
0.800
0.500
0.500
00630
N02&N03
N-TOTAL
MG/L
0.090
0.090
0.130
0.140
00671
PHOS-OIS
ORTHO
MG/L P
0.002
0.004
0.003
6.003
-------
STORE! RETRIEVAL DATE 76/03/30
182806
39 03 18.0 086 2
MONROE RESERVOIR
18013 INDIANA
15.0 3
051891
11EPALES
0022 FEET DEPTH
DATE
FROM
TO
73/08/06
73/10/10
DATE
FROM
TO
73/08/06
73/10/10
TIME DEPTH
OF
DAY FEET
14 25 0000
14 25 0005
14 25 0018
12 00 0000
12 00 0005
12 00 0011
TIME DEPTH
OF
DAY FEET
14 25 0000
14 25 0005
14 25 0018
12 00 0000
12 00 0005
12 00 0011
00010
WATER
TEMP
CENT
26.2
25.2
23.7
21.8
20.7
20.4
00665
PHOS-TOT
MG/L P
0.059
0.050
0.056
0.061
0.046
0.081
00300
DO
MG/L
2.6
1.0
3.2
2.2
32217
CHLRPHYL
A
UG/L
6.4
4.6
00077 00094
TRANSP CNDUCTVY
SECCHI FIELD
INCHES MICROMHO
14 95
100
117
28 127
126
126
00400
PH
2111202
CLASS 00
00410 00610
T ALK NH3-N
CAC03 TOTAL
SU
7.10
6.60
6.60
7.00
6.80
6.80
MG/L MG/L
26 0
23 0
31 0
37 0
33 0
34 0
.130
.330
.340
.200
.240
.350
00625
TOT KJEL
N
MG/L
1
1
0
1
1
1
.000
.000
.600
.200
.000
.100
—
00630
N021N03
N-TOTAL
.MG/L
0.190
0.210
0.270
0.050
0.040
0.050
00671
PHOS-D1S
ORTHO
MG/L P
0.007
0.023
0.013
0.014
0.009
0.009
-------
APPENDIX E
TRIBUTARY and WASTEWATER
TREATMENT PLANT DATA
-------
STORE! RETRIEVAL DATE 76/03/30
1828A1
39 00 16.0 086 30 30.0 4
SALT CREEK
18 7.5 CLEAR CREEK
0/MONROE RES 051891
BANK BELO DAM AT GAGING STATION
11EPALES 2111204
0000 FEET DEPTH CLASS 00
DATE
FROM
TO
73/06/09
73/07/11
73/08/14
73/09/05
73/10/04
73/11/08
73/12/18
74/02/09
74/02/24
74/03/09
74/03/23
74/04/06
74/05/05
00630 00625
TIME DEPTH N02&N03 TOT KJEL
OF N-TOTAL N
DAY FEET
14
15
10
09
14
12
10
15
15
15
14
14
11
25
05
03
00
34
30
00
15
30
15
30
30
00
MG/L
0.210
0.042
0.018
0.010K
0.028
0.068
0.148
0.252
0.340
0.336
0.384
0.360
0.312
MG/L
0
1
0
0
0
0
0
0
0
0
0
0
0
.500
.400
.630
.660
.800
.500
.300
.500
.600
.200
.300
.600
.200
00610 00671 00665
NH3-N PHOS-DIS PHOS-TOT
TOTAL ORTHO
MG/L
0.087
0.059
0.180
0.140
0.340
0.168
0.064
0.055
0.040
0.015
0.012
0.040
0.030
MG/L P
0.005K
0.006
0.014
0.005K
0.006
0.005K
0.005K
0.005K
0.010
0.005
0.005K
0.005K
0.005
MG/L P
0.010
0.015
0.025
0.020
0.025
0.010
0.005K
0.005
0.015
0.035
0.010
0.015
0.005
K VALUE KNOWN TO BE
LESS THAN INDICATED
-------
STORET RETRIEVAL DATE 76/03/30
1828dl
39 01 20.0 086 15 37.0 4
S FOKK SALT CR
18 7.5 ELKINSVILLE
I/MONROE RES 051891
RJ BROG JUST NE OF MAUMEE
11EPALES 2111204
0000 FEET DEPTH CLASS 00
DATE
FROM
TO
73/06/09
73/07/11
73/08/14
73/09/05
73/10/04
73/11/08
73/12/18
74/01/16
74/02/09
74/02/24
74/03/09
74/03/23
74/04/06
7^/05/05
00630 00625
TIME DEPTH N02&N03 TOT KJEL
OF N-TOTAL N
DAY FEET
15
11
11
14
13
12
11
10
11
14
10
11
10
14
55
05
40
50
45
00
30
30
00
35
35
00
55
15
MG/L
0
0
0
0
0
0
0
0
0
0
0
0
0
0
.480
.800
.220
.023
.022
.010K
.830
.680
.588
.390
.552
.560
.450
.240
MG/L
0.
1.
0.
0.
1.
0.
0.
0.
0.
0.
0.
0.
0.
0.
940
200
370
750
100
550
200
500
300
300
400
200
300
200
00610 00671 00665
NH3-N PHOS-DIS PHOS-TOT
TOTAL ORTHO
MG/L
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
110
336
075
055
198
030
052
104
047
040
060
020
070
035
MG/L
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
P
007
026
008
005K
014
024
005K
010
005
005
010
005K
005K
005
MG/L P
0.030
0.030
0.030
0.050
0.015
0.080
0.005
0.035
0.070
0.015
0.025
0.020
K VALUE KNOWN TO tfE
LESS THAN INDICATED
-------
STORE! RETRIEVAL DATE 76/03/30
1828C1
39 05 35.0 086 12 30.0 4
MIDDLE FORK SALT CR
18 7.5 STORr
I/MONROE RES 051891
ST HWY 135 BRDG .5 MI SE OF STORY
11EPALES 2111204
0000 FEET DEPTH CLASS 00
DATE
FROM
TO
73/06/09
73/07/11
73/08/14
73/09/05
73/10/04
73/11/08
73/12/18
74/01/16
74/02/09
74/02/24
74/03/09
74/03/23
74/04/06
74/05/05
00630
00625
TIME DEPTH N02&N03 TOT KJEL
OF
DAY FEET
15 20
10 20
11 10
14 10
13 10
11 ?7
11 00
09 55
10 30
14 00
10 10
10 15
10 15
13 40
N-TOTAL
MG/L
1.060
0.740
0.078
0.010K
0.011
0.010K
0.590
0.450
0.520
0.440
0.410
0.504
0.360
0.152
N
MG/L
0.560
0.300
0.460
0.980
0.660
0.550
0.800
0.200
0.300
1.600
0.200
0.200
0.200
0.100K
00610
NH3-N
TOTAL
MG/L
0.054
0.252
0.088
0.034
0.075
0.032
0.050
0.044
0.040
0.060
0.020
0.015
0.030
0.020
00671
PHOS-DIS
ORTHO
MG/L P
0.005K
0.007
0.007
0.007
0.021
0.005K
0.008
0.005K
0.005
0.005
0.005K
0.005K
0.005K
00665
PHOS-TOT
MG/L P
0.020
0.015
0.030
0.055
0.035
0.040
0.005K
0.025
0.005
0.030
0.035
0.005K
0.005
0.055
K VALUE KNOWN TO BE
LESS THAN INDICATED
-------
STORET RETRIEVAL DATE 76/03/30
182801
39 05 30.0 086 13 42.0 4
GRAVEL CR
18 7.5 STORY
T/MONROE RES 051891
ELKINSVILLE RO BRUG 1.5 MI WSrt OF STORY
11EPALES 2111204
0000 FEET DEPTH CLASS 00
DATE
FROM
TO
73/06/09
73/07/11
73/08/14
73/09/05
73/10/04
73/11/08
73/12/18
74/01/16
74/02/09
74/02/24
74/03/09
74/03/23
74/04/06
74/05/05
00630 00625
TIME DEPTH N02&N03 TOT KJEL
OF N-TOTAL N
DAY FEET
15
09
11
14
13
11
10
09
11
13
11
10
11
15
05
55
00
00
00
15
50
45
30
45
10
00
?8
00
MG/L
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
850
580
140
010K
010K
010K
550
390
460
336
370
420
312
116
MG/L
0.
3.
0.
0.
1.
0.
0.
0.
0.
0.
0.
0.
0.
0.
240
000
440
657
100
850
400
300
100
400
100
200
300
200
00610 00671 00665
NH3-N PHOS-DIS PHOS-TOT
TOTAL ORTHO
MG/L
0.
9.
0.
0.
0.
0.
0.
0.
Oe
0.
0.
0.
0.
0.
052
189
084
130
176
020
064
040
020
030
020
015
035
015
MG/L
0.
0.
0.
0.
0.
0*
0.
0.
0.
0.
0.
0.
0.
0*
P
005K
007
005K
005K
015
008
005K
008
005K
005
005
005K
005K
005K
MG/L P
0.020
0.020
0.030
0.030
0.050
0.020
0.035
0.005K
0.015
0.045
0.010
0.010
0.010
K VALUE KNOWN TO BE
LESS THAN INDICATED
-------
STORE! RETRIEVAL DATE 76/03/30
1828E1
39 06 30.0 086 18 46.0 4
CROOKED CR
18 7.5 ELKINSVILLE
T/MONROE RES 051891
CROOKE CREEK RD NEAR CROOKED CREEK CH
11EPALES 2111204
0000 FEET DEPTH CLASS 00
DATE
FROM
TO
73/06/09
73/07/11
73/08/14
73/09/05
73/10/04
73/11/08
73/12/18
74/01/16
74/02/09
74/02/24
74/03/09
74/03/23
74/04/06
74/05/05
00630 00625
TIME DEPTH N02&N03 TOT KJEL
OF N-TOTAL N
DAY FEET
10
12
11
10
13
11
11
10
13
13
12
15
12
09
20
45
08
40
05
00
20
38
00
10
17
45
35
30
MG/L
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
126
105
029
017
010K
390
208
164
200
140
140
148
104
040
MG/L
3.200
4.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
300
240
220
400
150
100K
200
350
400
100K
200
100K
200
00610 00671 00665
NH3-N PHOS-DIS PHOS-TOT
TOTAL ORTHO
MG/L
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
069
147
031
026
042
018
024
020
015
015
010
015
020
010
MG/L
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
P
005K
007
005K
005K
005K
007
005K
005K
005K
005K
005
005K
005K
005K
MG/L P
0.010
0.010
0.010
O.Ui-5
0.020
O.Olb
0.005K
0.010
0.010
0.025
0.030
0.005
0.005K
0.005K
K VALUE KNOrtN TO BE
LESS THAN INDICATED
-------
STORE! RETRIEVAL DATE 76/03/30
1828F1
39 09 30.0 086 20 13.0 4
N FORK SALT CR
18 7.5 BELMONT
I/MONROE RES 051893
ST HWr 46 BROG 1 MI NE OF BELMONT
11EPALES 2111204
0000 FEET DEPTH CLASS 00
DATE
FROM
TO
73/06/09
73/07/11
73/08/14
73/09/05
73/10/04
73/11/08
73/12/18
74/01/16
74/02/09
74/02/24
74/03/09
74/03/23
74/04/06
74/05/05
00630 00625
TIME DEPTH N02&N03 TOT KJEL
OF N-TOTAL N
DAY FEET
11
12
11
11
12
11
11
09
10
12
14
11
16
12
09
00
20
45
15
40
00
40
45
50
40
?0
55
00
15
10
MG/L
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
.189
.480
.132
.037
.010K
.014
.540
.730
.500
.360
.240
.410
.384
.224
.132
MG/L
0.
1.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
640
900
500
330
745
500
200
400
200
600
700
200
400
300
100K
00610 00671 0066S
NH3-N PHOS-DIS PHOS-TOT
TOTAL ORTHO
MG/L
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
066
200
115
054
024
016
044
024
032
045
020
015
020
030
025
MG/L
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
P
008
014
007
006
052
012
005K
008
005K
010
010
005
005
005
MG/L P
0.030
0.040
0.045
0.037
0.055
0.085
0.035
0.005K
0.025
0.01C
0.045
0.055
0.020
0.045
0.030
K VALUE KNOrtN TO d£
LESS THAN INDICATED
-------
STORET RETRIEVAL DATE 76/03/30
18Z8G1
39 09 30.0 086 20 16
LOWE* SCHOONER CR
18 7.5 BELMONT
T/MONROE RES
BANK 200 YDS
HEPALES
0 4
051892
E OF ST HWY 46
2111204
0000 FEET DEPTH CLASS 00
DATE
FROM
TO
73/06/09
73/07/11
73/08/14
73/09/05
73/10/04
73/11/08
73/12/18
74/01/16
74/02/09
74/02/24
74/03/09
74/03/23
74/04/06
74/05/05
00630 00625
TIME DEPTH N02&N03 TOT KJEL
OF N-TOTAL N
DAY FEET
10
12
11
11
12
11
11
10
12
14
11
16
12
09
53
10
45
12
45
05
45
55
35
10
50
01
05
00
MG/L
0
0
0
0
0
0
0
0
0
0
0
0
0
0
.294
.510
.132
.031
.010K
.010K
.580
.480
.410
.240
.290
.352
.260
.096
MG/L
2.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
600
780
500
370
750
500
200
100K
300
600
100
200
150
100K
00610 00671 00665
NH3-N PHOS-DIS PhOS-TOT
TOTAL ORTHO
MG/L
0.069
0.100
0.126
0.063
0.023
0.015
0.060
0.012
0.030
0.065
0.015
0.015
0.035
0.015
MG/L P
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
G.
005K
009
008
038
005K
005K
005K
005K
005
005
005K
005K
MG/L P
0
0
0
0
0
0
0
0
0
0
0
0
0
0
.020
.020
.045
.050
.060
.070
.010
.005
.OOSK
.030
.035
.008
.010
.010
K VALUE KNOWN TO BE
LESS THAN INDICATED
-------
STORE! RETRIEVAL DATE 76/03/30
1826H1
39 10 46.0 086 23 35.0 4
BRUMMETT CK
18 7.5 UNIONVILLE
T/MONROE RES 051892
6RUMMETT CR RO BRDG 5 MI S OF UNIONVILLE
11EPALES 2111204
0000 FEET DEPTH CLASS 00
DATE
FROM
TO
73/06/09
73/07/11
73/08/14
73/09/05
73/10/04
73/11/08
73/12/18
74/01/16
74/02/09
74/02/24
74/03/09
74/03/23
74/04/06
74/05/05
00630 00625
TIME DEPTH N02S.N03 TOT KJEL
OF N-TOTAL N
DAY FEET
09
13
12
10
13
10
11
10
13
12
12
15
12
09
47
10
10
21
35
30
00
15
20
45
40
22
50
50
MG/L
0
0
0
0
0
0
0
0
0
0
0
0
0
0
.200
.240
.120
.138
.220
.108
.780
.500
.430
.264
.330
.330
.232
.080
MG/L
1.
0.
0.
1.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
540
420
870
900
850
300
100K
200
200
300
100
100
200
100K
00610 00671 00665
NH3-N PHOS-DIS PHOS-TOT
TOTAL ORTHO
MG/L
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
072
042
088
520
180
055
024
040
020
015
010
010
020
010
MG/L P
0.005K
0.006
0.005K
0.014
0.005K
0.020
0.005K
0.016
0.005K
0.005K
0.005
0.005K
0.005K
0.005K
MG/L P
0
0
0
0
0
0
0
0
0
0
0
0
0
.005K
.015
.020
.040
.025
.OOSK
.025
.005K
.020
.037
.005K
.005K
.005*
K VALUE KNOWN TO BE
LESS THAN INDICATED
-------
STORE? RETRIEVAL DATE 76/03/30
1828J1
39 09 50.0 086 25 10.0 4
STEPHENS CHEEK
18 7.5 UNIONVILLE
T/MONROE KES 051892
ST HWY 46 8RDG 3 Ml E OF BLOOMINGTON
11EPALES 2111204
0000 FEET DEPTH CLASS 00
DATE
FROM
TO
73/06/09
73/07/11
73/08/14
73/09/05
73/10/04
73/11/08
73/12/18
74/01/16
74/02/09
74/02/24
74/03/09
74/03/23
74/04/06
74/05/05
00630 006P5
TIME DEPTH N02&.N03 TOT KJEL
OF N-TOTAL N
DAY FEET
09
13
11
10
13
10
10
10
13
13
12
15
13
10
15
25
45
10
45
20
50
05
30
06
50
10
00
05
MG/L
0
C
0
1
1
1
0
0
0
0
0
0
0
0
.400
.930
.660
.500
.640
.200
.792
.690
.616
.440
.588
.560
.360
.168
MG/L
2.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
800
770
710
560
120
100K
100
700
500
400
100K
100
300
1COK
00610 00671 00665
NH3-N PHOS-DIS PHOS-TOT
TOTAL ORTHO
MG/L
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
088
084
060
100
050
020
036
044
020
020
005K
005
035
015
MG/L
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
p
005K
Oil
005K
005K
005K
003
005K
008
005K
005K
005
OOSK
005K
005
MG/L P
0.010
0.015
0.025
0.025
0.015
0.020
0.005K
0.010
0.005K
0.022
0.030
0.005K
0.005
0.005
K VALUE KNOWN TO BE
LESS THAN INDICATED
-------
STORET RETRIEVAL DATE 76/03/30
1828K1
39 06 55.0 086 28 12.0 4
MOORE CREEK
18 7.5 ALLEN CREEK
T/MONROE RES 051891
MOORE CR RD 8ROG 1 MI SE MT CALVARY CH
HEPALES 2111204
0000 FEET DEPTH CLASS 00
DATE
FROM
TO
73/06/09
73/07/11
73/08/14
73/09/05
73/10/04
73/11/08
73/12/18
74/01/16
74/02/09
74/02/24
74/03/09
74/03/23
74/04/06
74/05/05
00630 00625
TIME DEPTH N02&N03 TOT KJEL
OF N-TOTAL N
DAY FEET
11
14
10
09
14
11
10
09
14
15
!<*
14
13
10
23
40
30
51
02
55
20
15
45
50
40
50
55
30
MG/L
0
0
0
0
0
0
0
0
0
0
0
0
0
0
.089
.231
.027
.010K
.031
.076
.690
.168
.570
.420
.530
.430
.368
.168
MG/L
1.
1.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
260
050
800
400
420
100K
100
300
200
200
100
200
100
100K
00610 00671 00665
NH3-N PHOS-DIS PHOS-TOT
TOTAL ORTHO
MG/L
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
064
068
027
016
025
016
024
044
020
015
005K
005
025
015
MG/L P
0.005K
O.OC5K
0.005K
0.005K
0.005K
0.005K
0.005K
0.005K
0.005K
0.005K
0.005K
0.005K
0.005K
0.005K
MG/L P
0
0
0
0
0
0
0
0
0
0
0
0
0
0
.040
.020
.025
.015
.015
.005K
.005K
.010
.005K
.020
.025
.005K
.005K
.005K
K VALUE KNOWN TO BE
LESS THAN INDICATED
-------
STORE! RETRIEVAL DATE 76/03/30
182821 PD182821 P000280
39 02 55.0 086 26 00.0 4
RANSBURG BSA
18 7.5 ALLEN CREEK
D/MONROE RESERVOIR 051891
MONROE RESERVOIR
HEPALES 2141204
0000 FEET DEPTH CLASS 00
DATE
FROM
TO
73/06/05
73/07/09
73/08/06
TIME DEPTH
OF
DAY FEET
09 30
14 00
12 00
00630
N02&N03
N-TOTAL
MG/L
0.030
0.030
0.110
00625
TOT KJEL
N
MG/L
4.400
5.400
4.600
00610
NH3-N
TOTAL
MG/L
0.210
0.200
0.210
00671
PHOS-DIS
ORTHO
MG/L P
0.138
0.087
0.570
00665
PHOS-TOT
MG/L P
1.100
0.480
1.200
50051 50053
FLOW CONDUIT
RATE FLOW-MGD
INST MOD MONTHLY
0.015
-------
STORET RETRIEVAL DATE 76/03/30
182831 P0182831 P000560
39 01 13.0 086 27 07.0 4
HAROIN RIDGE
18 7.5 ALLENS CREEK
D/MONROE RESERVOIR osi89i
MONROE RESERVOIR
11EPALES 2141204
0000 FEET DEPTH CLASS 00
DATE
FROM
TO
73/07/05
CP(T)-
73/07/05
73/08/06
CP '. T ) -
73/08/06
73/09/11
CP
-------
STORE! RETRIEVAL DATE 76/03/30
182841 AS182841 P002053
39 01 00.0 086 29 00.0 4
FAIRFAX
18 7.5 ALLENS CREEK
D/MONROE RESERVOIR 051891
MONROE RESERVOIR
11EPALES 2141204
0000 FEET DEPTH CLASS 00
DATE
FROM
TO
73/06/12
73/07/0?
73/08/15
73/09/06
73/10/04
73/11/08
74/03/15
74/04/04
74/05/03
74/06/03
74/07/08
74/08/01
74/09/03
TIME DEPTH
OF
DAY FEET
13 00
11 00
11 00
09 00
09 00
09 00
08 45
09 40
09 30
08 45
09 00
09 00
13 45
00630
N02&N03
N-TOTAL
MG/L
0.230
0.040
0.032
0.092
0.050
0.050
0.040
1.520
0.080
0.200
0.120
0.040
0.040
00625
TOT KJEL
N
MG/L
13.800
5.600
21.000
21.000
31.500
18.500
1.700
7.700
4.900
17.000
21.000
40.000
6.500
00610
NH3-N
TOTAL
MG/L
0.260
0.280
4.500
11.000
6.200
0.160
1.050
1.550
4.000
13.500
15.800
00671
PHOS-DIS
ORTHO
MG/L P
2.900
2.800
6.500
6.440
3.000
6.400
1.350
1.400
2.600
4.600
5.400
6.000
00665
PHOS-TOT
MG/L P
4.800
3.700
7.400
5.800
8.100
1.930
2.400
1.900
4.300
5.400
8.200
0.990
50051 50053
FLOW CONDUIT
RATE FLOW-MGD
INST MGD MONTHLY
-------
STORE! RETRIEVAL DATE 76/03/30
182851 TF182851 P002200
39 05 00.0 086 26 10.0 4
PAYNETOWN
18 7.5 ALLENS CHEEK
D/MONKOE RESERVOIR 051891
MONROE RESERVOIR
11EPALES 2141204
0000 FEET DEPTH CLASS 00
DATE
FROM
TO
73/06/12
73/07/02
73/08/15
73/09/04
73/10/04
74/05/03
74/06/03
74/07/08
74/08/09
74/09/04
TIME DEPTH
OF
DAY FEET
09 00
13 30
09 00
09 00
10 00
15 00
11 15
11 00
10 45
09 45
00630
N02&N03
N-TOTAL
MG/L
1.470
4.900
15.400
16.000
7.100
0.040
5.880
20.000
10.000
11.800
00625
TOT KJEL
N
MG/L
5.200
4.250
21.000
8.000
25.000
2.900
8.000
17.000
19.000
21.500
00610
NH3-N
TOTAL
MG/L
2.500
1.600
9.400
14.000
0.130
2.100
13.250
10.000
15.000
00671
PHOS-DIS
ORTHO
MG/L P
1.900
2.300
6.400
7.400
0.650
1.800
4.900
6.800
6.800
00665
PHOS-TOT
MG/L P
2.000
2.300
2.600
7.100
7.700
1.100
2.500
4.900
7.350
6.800
50051 50053
FLOW CONDUIT
RATE FLOW-MOD
INST MGD MONTHLY
-------
STORET RETRIEVAL DATE 76/03/30
1828AA AS1828AA
39 12 15.0 086 15 18.0 4
NASHVILLE
18 7.5 BELMONT
T/MONROE RESERVOIR 051892
SALT CREEK
11EPALES 2141204
0000 FEET DEPTH CLASS 00
DATE
FROM
TO
73/09/06
73/10/11
73/11/08
73/12/11
74/01/12
74/02/13
74/03/13
TIME DEPTH
OF
DAY FEET
09 00
09 00
09 00
10 00
13 00
15 30
10 00
00630
N02&N03
N-TOTAL
MG/L
0.200
0.020
0.110
0.200
0.240
0.560
0.040
00625
TOT KJEL
N
MG/L
40.000
43.000
37.000
22.000
6.900
22.000
8.000
00610
NH3-N
TOTAL
MG/L
6.100
8.600
6.600
2.300
0.750
2.000
00671
PHOS-DIS
ORTHO
MG/L P
8.600
9.500
7.000
2.300
2.520
2.900
00665
PHOS-TOT
MG/L P
14.850
15.700
7.400
4.400
7.300
2.800
50051
FLOW
RATE
INST MGD
0.150
0.150
0.150
0.150
0.150
0.150
0.150
50053
CONDUIT
FLOW-MOO
MONTHLY
0.150
0.150
0.150
0.150
0.150
0.150
------- |