U.S. ENVIRONMENTAL PROTECTION AGENCY
NATIONAL EUTROPHICATION SURVEY
WORKING PAPER SERIES
REPORT
ON
CATARACT U\KE
OWEN AND PUTOAM COUNTIES
INDIANA
EPA EGION V
WORKING PAPER No, 324
CORVALLIS ENVIRONMENTAL RESEARCH LABORATORY - CORVALLIS, OREGON
and
ENVIRONMENTAL MONITORING & SUPPORT LABORATORY - LAS VEGAS, NEVADA
699-440
-------
0_
REPORT
ON
CATARACT LAKE
OWEN AND PUIW1 COUNTIES
INDIANA
EPA REGION V
tr> WORKING PAPER No, 324
^t
WITH THE COOPERATION OF THE
INDIANA STATE BOARD OF HEALTH
AND THE
INDIANA NATIONAL GUARD
, 1976
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CONTENTS
Page
Foreword i i
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 Sumnary 5
IV. Nutrient Loadings 9
V. Literature Reviewed 14
VI. Appendices 15
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n
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(e)>, water
quality criteria/standards review {§303(c)K 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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iii
Beyond the single lake analysis, broader based correlations
between nutrient concentrations (and loading) and trophic condition
are being made to advance the rationale and data base for refine-
ment of nutrient water quality criteria for the Nation's freshwater
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 the U.S. Environmental Protection
Agency and to augment plans implementation by the states.
ACKNOWLEDGMENTS
The staff of the National Eutrophication Survey (Office of
Research and Development, U.S. Environmental Protection Agency)
expresses sincere appreciation to the New Jersey Department of
Environmental Protection for professional involvement and to the
New Jersey National Guard for conducting the tributary sampling
phase of the Survey.
Douglas Clark, Chief of the Bureau of Water Quality Planning
and Management, Mr. Frank Takacs, New Jersey National Eutrophication
Survey Coordinator, Principal Environmental Specialist, and
Robert Kotch, Senior Environmental Engineer, 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 William R. Sharp, Former Chief of Staff, Major
General Wilfred G. Menard, Jr., Chief of Staff, and Project Officer
Colonel Herbert D. Ruhlin, who directed the volunteer efforts of
the New Jersey National Guardsmen, are also gratefully acknowledged
for their assistance to the Survey.
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iv
NATIONAL EUTROPHICATION SURVEY
STUDY LAKES
STATE OF NEW JERSEY
LAKE NAME
Budd Lake
Duhernal Lake
Farrington Lake
Greenwood Lake
Lake Hopatcong
Lake Musconetcong
Oradell Reservoir
Paulinskill Lake
Pinecliff Lake
Pompton Lakes
Spruce Run Reservoir
Union Lake
Wanaque Reservoir
COUNTY
Morris
Middlesex
Middlesex
Passaic, N.J.;
Orange, N.Y.
Morris, Sussex
Morris, Sussex
Bergen
Sussex
Passaic
Passaic
Hunterdon
Cumberland
Passaic
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CATARACT LAKE
(g) Tributary Sampling Site
X Lake Sampling Site
• Sewage Treatment Facility
ODl"ainage Area Boundary
? , . ,?
Scale
5 Mi.
3945—
Map Location
Ind.
86-45'
86'30'
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CATARACT LAKE
STORET NO. 1805
I. CONCLUSIONS
A. Trophic Condition:
Survey data indicate that Cataract Lake is eutrophic. It
ranked nineteenth in overall trophic quality when the 27 Indiana
lakes sampled in 1973 were compared using a combination of six
parameters*. Sixteen lakes had less and one had the same median
total phosphorus, 16 had less and one had the same median dis-
solved phosphorus, 22 had less median inorganic nitrogen, ten
had less mean chlorophyll a^ and 18 had greater mean Secchi disc
transparency. Hypolimnetic depletion or near-depletion of dis-
solved oxygen occurred at stations 2 and 3 in August and October.
Survey limnologists noted algal concentrations in May at sta-
tions 1 and 3.
Survey data compare well with data obtained in a previous
study (Anonymous, 1974).
B. Rate-Limiting Nutrient:
The algal assay results indicate that Cataract Lake was phos-
phorus limited at the time the sample was collected (05/10/73).
The lake 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—During the sampling year, Cataract Lake
received a total phosphorus loading over four times that pro-
posed by Vollenweider (Vollenweider and Dillon, 1974) as a
eutrophic loading (see page 13). The only measured point source,
the Cloverdale wastewater treatment plant, contributed 2% of
that load. However, it is probable that known but unmeasured
point sources contributed significantly to the total phosphorus
load (see below), and an adequate assessment of nutrient con-
trollability cannot be made until the magnitude of the nutrient
contribution from these sources can be determined.
Reportedly (McAhron, 1973), a hog farm impacts Ferguson Branch
just downstream from station E-l and another one impacts Doe Creek
upstream from station B-l (see map, page v). On the basis of the
differences in the phosphorus export rates of the Cataract Lake
tributaries, it is conservatively estimated that these two point
sources contributed in excess of 2,000 kg of total phosphorus to
the lake during the sampling year.
2. Non-point sources—During the sampling year, the phos-
phorus export rate of Mill Creek was somewhat high as compared
to the rates of other Indiana streams sampled; however, the export
N/P ratio indicates that if point sources are present in the drain-
age, they are minor.
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3
On the other hand, the phosphorus export rate of Doe Creek
was over twice that of Mill Creek, and it is probable that the
difference is attributable to the unmeasured point source noted
above. Also, the phosphorus export rate of Ferguson Creek at
station E-2 is over three times the rate in this stream at sta-
tion D-l and in Ferguson Branch at station E-l, and the differ-
ence likely is due to the point source impacting this stream
downstream from station E-l.
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II. LAKE AND DRAINAGE BASIN CHARACTERISTICS1"
4-4.
A. Lake Morphometry :
1. Surface area: 5.66 kilometers2.
2. Mean depth: 6.1 meters.
3. Maximum depth: 17.0 meters.
4. Volume: 34.538 x 106 m3.
5. Mean hydraulic retention time: 50 days.
B. Tributary and Outlet:
(See Appendix C for flow data)
1. Tributaries -
Drainage Mean flow
Name area (km2)* (m3/sec)*
Mill Creek 657.3 7.14
Doe Creek 34.4 0.32
Ferguson Creek (E-2)** 24.9 0.11
Minor tributaries &
immediate drainage - 39.7 0.40
Total 756.3 7.97
2. Outlet -
Mill Creek 762.0*** 7.97
C. Precipitation****:
1. Year of sampling: 138.4 centimeters.
2. Mean annual: 103.1 centimeters.
t Table of metric conversions—Appendix B.
tt Winters, 1975.
* For limits of accuracy, see Working Paper No. 175, "...Survey Methods,
1973-1976".
** Includes areas of D-l and E-l; see map, page v.
*** Includes area of lake; outflow adjusted to equal sum of inflows.
**** See Working Paper No. 175.
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5
III. LAKE WATER QUALITY SUMMARY
Cataract Lake 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 three stations on the lake (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, a single 18.9-liter depth-
integrated sample was composited for algal assays. Also each time,
a depth-integrated sample was collected from each of the stations for
chlorophyll a_ analysis. The maximum depths sampled were 3.0 meters
at station 1, 11.0 meters at station 2, and 11.0 meters at station 3.
The sampling results are presented in full in Appendix D and are
summarized in the following table.
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PARAMETER
TEMP (C)
DISS OXY (MG/L)
CNDCTVY (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 ( 5/10/731
3 SITES
RANGE
11.9
4.8
380.
7.6
138.
0.031
0.009
2. 050
0.050
0.400
3.190
3. 750
5.9
0.3
- 19.2
- 10.0
- 430.
8.3
- 160.
- 0.109
- 0.037
- 2.880
- 0.310
- 1.100
- 3.110
- 3.800
- 12.5
1.5
MEAN
16.1
8.2
398.
7.9
147.
0.058
0.016
2.611
0.121
0.738
2.732
3.349
9.5
1.1
MEDIAN
17.0
8.7
395.
8.0
146.
0.046
0.013
2.780
0.090
0.700
2.850
3.380
10.1
1.5
CHEMICAL CHARACTERISTICS FOR CATARACT
STORET CODE 1805
2ND SAMPLING ( 8/ 3/73)
3 SITES
RANGE
21.9
0.1
230.
7.2
93.
0.034
0.008
0.650
0.070
0.700
0.760
1.950
4.4
0.3
- 27.9
- 10.8
- 399.
8.9
- 184.
- 0.201
- 0.049
- 1.830
- 0.470
- 1.500
- 1.910
- 2.730
- 19.6
0.9
MEAN
25.1
3.1
281.
7.9
116.
0.082
0.026
1.225
0.184
1.108
1.409
2.333
10.0
0.6
MEDIAN
24.4
1.0
262.
7.9
103.
0.067
0.022
1.250
0.110
1.100
1.460
2.375
6.0
0.7
LAKE
3RD SAMPLING (10/10/73)
3 SITES
RANGE
19.0
0.0
293.
7.0
124.
0.032
0.007
0.030
0.100
0.700
0.140
0.740
7.2
0.3
- 24.5
- 13.0
- 410.
8.8
- 200.
- 0.268
- 0.019
- 0.060
- 4.880
- 6.300
- 4.930
- 6.350
- 21.1
1.3
MEAN
22.2
3.9
328.
7.8
146.
0.093
0.011
0.047
0.843
1.755
0.890
1.802
12.7
0.8
MEDIAN
22.3
2.0
301.
7.7
130.
0.049
0.010
0.050
0.240
1.300
0.300
1.330
9.9
0.8
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B. Biological characteristics:
1. Phytoplankton -
Sampling
Date
05/10/73
08/08/73
10/10/73
2. Chlorophyll a_ -
Sampling
Date
05/10/73
08/08/73
10/10/73
Dominant
Genera
1.
2.
3.
4.
5.
1.
2.
3.
4.
5.
1.
2.
3.
4.
5.
Centric diatoms
Flagellates
Asterionella sp.
Cryptomonas SJD.
Nitzschia sp_.
Other genera
Total
Oscillator! a sp.
Anabaena sp.
Melosira sp.
Aphanizomenon sp.
Flagellates
Other genera
Total
Aphanizomenon sp.
Oscillatoria s£.
Anabaena sp.
Flagellates
Cyclotella sp.
Other genera
Algal Units
per ml
9,160
Total
Station
Number
1
2
3
1
2
3
1
2
3
1,781
1,957
814
780
191
104
190
4,036
Chlorophyll a
(ug/1)
5.9
10.1
12.5
19.6
4.4
6.0
9.9
21.1
7.2
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8
C. Limiting Nutrient Study:
1. Autoclaved, filtered, and nutrient spiked -
Ortho P Inorganic N Maximum yield
Spike (mg/1) Cone, (mg/1) Cone, (mg/1) (mg/l-dry wt.)
Control 0.010 2.710 1.2
0.050 P 0.060 2.710 14.6
0.050 P + 1.0 N 0.060 3.710 16.8
1.0 N 0.010 3.710 1.4
2. Discussion -
The control yield of the assay alga, Selenastrum capri-
cornutum, indicates that the potential primary productivity
of Cataract Lake was moderate at the time the assay sample
was collected. The results also indicate the lake was phos-
phorus limited at that time. Note that the yield with the
addition of nitrogen alone was not significantly different
from the control yield, but the yield with the addition of
orthophosphorus alone was over twelve times the control yield.
The lake data indicate Cataract Lake was phosphorus limi-
ted at all sampling times. The mean inorganic nitrogen
to orthophosphorus ratios were 54 to 1 or greater, and phos-
phorus limitation would be expected.
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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 nutrient loads,
in kg/km2/year, in Ferguson Creek at station D-l and multiplying by
the ZZ area in km2.
The operator of the Cloverdale wastewater treatment plant provided
monthly effluent samples and corresponding flow data.
* See Working Paper No. 175.
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10
A. Waste Sources:
1. Known municipal* -
Pop. Mean Flow Receiving
Name Served Treatment (m3/d) Water
Cloverdale 1,000 act. sludge 260.3 Rabbit Run
2. Known industrial - Reportedly (McAhron, 1973), a hog farm
impacts Ferguson Branch just below station E-l, and another
impacts Doe Creek above station B-l. These point sources
were not measured, and their impact on Cataract Lake is not
known.
* Davis, 1973.
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11
B. Annual Total Phosphorus Loading - Average Year:
1. Inputs -
kg P/ % of
Source yr total
a. Tributaries (non-point load) -
Mill Creek 27,115 84.7
Doe Creek 2,860 8.9
Ferguson Creek (E-2) 890 2.8
b. Minor tributaries & immediate
drainage (non-point load) - 395 1.2
c. Known municipal STP's -
Cloverdale 635 2.0
d. Septic tanks* - 10 <0.1
e. Industrial - Unknown ?
f. Direct precipitation** - 100 0.3
Total 32,005 100.0
2. Outputs -
Lake outlet - Mill Creek 18,190
3. Net annual P accumulation - 13,815 kg.
* Estimate based on 40 lakeshore dwellings; see Working Paper No. 175.
** See Working Paper No. 175.
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12
C. Annual Total Nitrogen Loading - Average Year:
1. Inputs -
kg N/ % of
Source yr total
a. Tributaries (non-point load) -
Mill Creek 966,785 93.3
Doe Creek 40,405 3.9
Ferguson Creek (E-2) 10,505 1.0
b. Minor tributaries & immediate
drainage (non-point load) - 9,450 0.9
c. Known municipal STP's -
Cloverdale 2,390 0.3
d. Septic tanks* - 425 <0.1
e. Industrial - Unknown ?
f. Direct precipitation** - 6,110 0.6
Total 1,036,070 100.0
2. Outputs -
Lake outlet - Mill Creek 766,615
3. Net annual N accumulation - 269,455 kg.
D. Mean Annual Non-point Nutrient Export by Subdrainage Area:
Tributary kg P/km2/yr kg N/km2/yr N/P Ratio
Mill Creek 41 1,471 36/1
Doe Creek 83 1,175 14/1
Ferguson Creek
at E-2 36 422 12/1
at D-l 10 238 24/1
at E-l 13 329 25/1
* Estimate based on 40 lakeshore dwellings; see Working Paper No. 175.
** See Working Paper No. 175.
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13
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/m2/yr 5.65 2.44 183.1 47.6
Vollenweider phosphorus loadings
(g/m2/yr) based on mean depth and mean
hydraulic retention time of Cataract Lake:
"Dangerous" (eutrophic loading) 1.28
"Permissible" (oligotrophic loading) 0.64
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14
LITERATURE REVIEWED
Anonymous, 1972. Cataract Lake survey of July 31, 1972. IN Div.
Water Poll. Contr., Indianapolis.
Davis, Chester L., 1973. Treatment plant questionnaire (Cloverdale
STP). Cloverdale.
McAhron, Ron, 1973. Personal communication (livestock point sources
impacting Cataract Lake). IN Div. Water Poll. Contr., 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.
Winters, John, 1975. Personal communication (lake morphometry). IN
Div. Water Poll. Contr., Indianapolis.
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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
182M
1829
1836
1837
1839
1840
1841
1842
1843
1844
1845
1846
1847
1848
1849
1850
1851
1852
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
rflTMER 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
1.62C
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
43B
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
.667
.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
J4
17
.744
.950
.533
.778
.947
.167
.000
.500
.003
.211
.712
.917
.483
.050
.067
.867
.767
.480
.267
.078
.367
.578
.856
.100
.900
.467
.450
15-
MIN DO
15
11
15
15
15
15
14
15
15
15
IS
15
15
15
15
14
14
14
7
14
7
15
15
15
15
15
15
.000
.600
.000
.000
.000
.000
.600
.000
.000
.000
.000
.000
.000
.000
.000
.900
.800
.800
.600
.500
.000
.000
.000
.000
.000
.000
.000
MEOI
DISS ORTi
0.01 j
0.009
O.OOd
0.029
0.00'
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
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PERCENT OF LAKES WITH HIGHER VALUES 0
1841
1842
18*3
1844
1845
1646
1847
184S
1849
1850
1851
1852
1853
1854
1855
1856
1857
LAKE NAME
CATARACT LAi\E
GEIST RESERVOI*
JAMES LAKE
MISSISSINErfA RESERVOIR
MONROE RESERVOIR
MORSE RESERVOIR
MAWASEE LAKE
WEBSTER LAKE
WHITEWATER LAKE
WINONA LAKE
WESTLER LAKE
HITHER 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
MAHSH LAKE
HAMILTON LAKE
MEDIAN
TOTAL f
37
27
73
12
67
?3
94
67
19
50
50
50
77
85
62
94
100
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
1 9)
I 16)
< 17)
( 2)
( 18)
( 15)
( 251
( 21)
( 11)
( 13)
( 9)
( 13)
( 25)
< 22)
< a>
( 24)
( 23)
( 6)
( 31
( 4)
I 12)
( 19)
( 19)
( 0)
( 7)
( 1)
( 5)
1NJEX
NO
-------
LAKES RANKED 8Y INDEX NOS.
RANK LAKE CODE LAKE NAME INDEX NO
1 1836 WAWASEE LAKE 546
2 1847 OLIVER LAKE 501
3 1853 LAKE JAMES 486
4 184* TIPPECANOE LAKE 462
5 1843 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 334
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 GEIST 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
ZS 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
03/29/76
LAKE CODE 1805
CATARACT LAKE
TOTAL DRAINAGE AREA OF LAKE(SO KM)
SUB-DRAINAGE
TRIBUTARY AREA(SQ KM)
JAN
FEB
759.6
MAR
APR
MAY
NORMALIZED FLOWS(CMS)
JUN JUL AUG
SEP
OCT
NOV
DEC
MEAN
1805A1
1805A2
1805B1
1805D1
1805E1
1805E2
1805ZZ
762.0
657.3
34.4
6.7
6.5
11.7
43.0
7.39
11.10
0.396
0.074
0.071
0.133
0.510
13.79
12.06
0.481
0.096
0.091
0.164
0.623
13.25
13.42
0.708
0.142
0.136
0.241
0.878
14.84
12.06
0.651
0.130
0.125
0.224
0.821
10.53
8.33
0.425
0.082
0.079
0.142
0.538
9.40
7.65
0.311
0.062
0.062
0.110
0.396
6.80
3.79
0.193
0.037
0.037
0.065
0.235
1.64
1.25
0.065
0.011
0.008
0.020
0.082
1.95
1.93
0.062
0.011
0.011
0.020
0.079
3.06
1.30
0.065
0.011
0.011
0.020
0.085
5.89
5.61
0.170
0.034
0.031
0.057
0.210
5.49
7.67
0.311
0.062
0.062
0.108
0.396
7.79
7.14
0.319
0.063
0.060
0.108
0.403
SUMMARY
TOTAL DRAINAGE AREA OF LAKE =
SUM OF SUB-DRAINAGE AREAS =
759.6
759.6
TOTAL FLOW IN
TOTAL FLOW OUT
97.64
94.04
MEAN MONTHLY FLOWS AND DAILY FLOWS(CMS)
TRIBUTARY MONTH YEAR
1805A1
MEAN FLOW DAY
FLOW DAY
FLOW DAY
FLOW
180SA2
6
7
8
9
10
11
12
1
2
3
4
5
1
6
7
8
9
10
11
12
2
3
4
5
73
73
73
73
73
73
73
74
74
74
74
74
73
73
73
73
73
73
73
73
74
74
74
74
18.179
11.327
17.670
0.699
0.858
3.908
19.482
26.816
36.812
20.586
15.319
13.054
24.891
16.764
20.841
2.430
0.603
0.564
8.665
16.990
10.336
15.716
10.477
21.068
10
9
12
23
25
27
17
16
5
6
17
15
16
10
9
12
23
25
27
17
5
6
17
15
3.851
2.832
7.815
0.396
0.425
3.625
3.625
10.336
51.112 20
3.002 20
41.34J
19.539
29.450
4.786
2.407
2.180
0.340
0.311
39.077
2.407
4.361 20
20.133 20
3.823
65.978
36.812
26.391
16.367
8.155
-------
TRIBUTARY FLOW INFORMATION FOR INDIANA
03/29/76
LAKE CODE 1805
CATARACT LAKE
MEAN MONTHLY FLOWS AND DAILY FLOWS(CMS)
TRIBUTARY MONTH YEAR MEAN FLOW DAY
1805B1
180501
1805E1
1805E2
6
7
8
9
10
11
12
1
2
3
4
5
6
7
8
9
10
11
12
1
2
3
it
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
FLOW DAY
FLOW DAY
FLOW
0.906
1.133
0.133
0.034
0.031
0.481
0.934
1.359
0.566
0.850
0.566
1.133
0.176
0.221
0.025
0.006
0.006
0.091
0.178
0.261
0.108
0.164
0.110
0.221
0.170
0.212
0.025
0.006
0.006
0.088
0.173
0.252
0.105
0.159
0.105
0.212
0.311
0.396
0.045
0.011
0.011
0.159
0.311
0.453
0.190
0.283
0.193
0.396
10
9
12
23
25
27
17
16
5
6
17
15
10
9
12
23
25
27
17
16
5
6
17
IS
10
9
12
23
25
27
17
16
5
6
17
IS
10
9
12
23
25
27
17
16
5
b
17
IS
0.261
0.130
0.119
0.017
0.017
2.124
0.130
1.586
0.238
1.104
0.207
3.568
0.051
0.025
0.023
0.0
0.003
0.396
0.025
0.311
0.045
0.212
0.040
0.680
0.048
0.025
0.023
0.003
0.003
0.396
0.025
0.311
0.045
0.204
0.040
0.680
0.088
0.045
0.040
0.006
0.006
0.708
0.045
0.538
0.079
0.368
0.071
1.218
20
20
20
20
20
20
20
20
0.878
0.453
0.173
0.085
0.167
0.082
0.283
0.150
-------
TRIBUTARY FLOW INFORMATION FOR INDIANA
03/29/76
LAKE CODE 1805
CATARACT LAKE
MEAN MONTHLY FLOWS AND DAILY FLOWS(CMS)
TRIBUTARY
1805ZZ
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
1.133
1.416
0.164
0.040
0.037
0.595
1.161
1.699
0.708
1.076
0.708
1.444
10
9
12
23
25
27
17
16
5
6
17
15
FLOW DAY
0.311
0.164
0.147
0.023
0.020
2.633
0.164
1.982
0.283 20
1.359 20
0.258
4.446
FLOW DAY
FLOW
1.104
0.566
-------
APPENDIX D
PHYSICAL and CHEMICAL DATA
-------
STORE! RETRIEVAL DATE 76/03/30
180501
39 27 13.0 086 50 36.0 3
CATARACT LAKE
18119 INDIANA
051991
DATE
FROM
TO
73/05/10
73/08/08
73/10/10
DATE
FROM
TO
73/05/10
73/08/08
73/10/10
TIME
OF
DAY
15 05
15 05
15 05
13 00
13 00
13 00
16 20
TIME
OF
DAY
15 05
15 05
15 05
13 00
13 00
13 00
16 20
DEPTH
FEET
0000
0005
0010
0000
0005
0010
0000
DEPTH
FEET
0000
0005
0010
0000
0005
0010
0000
00010
WATER
TEMP
CENT
19.2
17.7
16.1
27.0
25.0
23.5
24.5
00665
PHOS-TOT
MG/L P
0.097
0.101
0.109
0.118
0.121
0.201
0.196
00300
DO
MG/L
8.
8.
2.
2.
13.
32217
11EPALES 2111202
0014 FtET DEPTH CLASS 00
00077 00094 00400 00410 00610 00625 00630 00671
TRANSP CNDUCTVY PH T ALK NH3-N TOT KJEL N02&N03 PHOS-DIS
SECCHI FIELD CAC03 TOTAL N N-TOTAL ORTHO
INCHES MICROMHO SU
9
9
8
6
0
12 395 8.30
400 8.10
395 7.90
12 263 8.70
301 7.50
399 7.60
12 373 8.80
MG/L
151
155
160
106
124
184
160
MG/L
0.070
0.090
0.170
0.090
0.220
0.320
0.140
MG/L
0.900
0.800
0.700
1.500
1.300
1.400
2.700
MG/L MG/L P
2.150 0
2.100 0
2.050 0
0.670 0
0.650 0
0.910 0
0.060 0
.012
.019
.027
.013
.013
.019
.019
CHLRPHYL
A
UG/L
5.
19.
9.
9
6
9
-------
STORET RETRIEVAL DATE 76/03/30
00010 00300
DATE TIME DEPTH WATER DO
FROM OF TEMP
TO DAY FEET CENT MG/L
73/05/10
73/08/08
73/10/10
DATE
FROM
TO
73/05/10
73/08/08
73/10/10
15
15
15
15
15
12
12
12
12
16
16
16
16
16
30
30
30
30
30
40
40
40
40
30
30
30
30
30
TIME
OF
DAY
15
15
15
15
15
12
12
12
12
16
16
16
16
16
30
30
30
30
30
40
40
40
40
30
30
30
30
30
0000
0006
0015
0022
0036
0000
0005
0015
0025
0000
0005
0015
0020
0026
DEPTH
FEET
0000
0006
0015
0022
0036
0000
0005
0015
0025
0000
0005
0015
0020
0026
17.6
17.4
16.2
15.3
11.9
27.9
27.7
23.8
23.1
23.0
22.4
22.3
22.0
21.3
00665
PHOS-TOT
MG/L P
0.036
0.055
0.043
0.045
0.062
0.034
0.059
0.069
0.066
0.049
0.042
0.038
0.087
0.146
9.5
8.6
5.4
4.8
10.8
0.9
1.0
6.8
5.0
0.2
0.6
32217
CHLRPHYL
A
UG/L
10.1
4.4
21.1
00077 00094
TRANSP CNDUCTVY
SECCHI FIELD
INCHES MICROMHO
60
28
32
390
390
395
430
420
261
260
242
367
299
298
301
318
410
180502
39 27 43.0 086 53 05.0 3
CATARACT LAKE
18119 INDIANA
051991
HEPALES
0040
00400
PH
SU
8.10
8.10
8.00
7.80
7.70
8.90
8.80
7.40
8.20
8.60
8.10
7.70
7.40
7.40
2111202
FEET DEPTH CLASS
00410
T ALK
CAC03
MG/L
144
143
146
160
150
98
99
100
167
130
128
138
139
187
00610
NH3-N
TOTAL
MG/L
0.070
0.080
0.090
0.150
0.260
0.100
0.070
0.080
0.360
0.100
0.150
0.220
0.610
0.550
00
00625
TOT KJEL
N
MG/L
0.800
0.700
0.800
0.700
1.100
1.500
1.300
0.700
0.900
0.800
0.800
0.700
1.300
1.400
00630
N02&N03
N-TOTAL
MG/L
2.820
2.820
2.780
2.590
2.560
1.230
1.170
1.830
1.160
0.040
0.040
0.040
0.030
0.050
00671
PHOS-DIS
ORTHO
MG/L P
0.011
0.013
0.013
0.018
0.022
0.008
0.020
0.049
0.030
0.007
0.008
0.008
0.009
0.014
-------
STORET RETRIEVAL DATE 76/03/30
DATE
FROM
TO
73/05/10
73/08/08
73/10/10
TIME DEPTH
OF
DAY FEET
15 50
15 50
15 50
15 50
15 50
12 15
12 15
12 15
12 15
12 15
17 00
17 00
17 00
17 00
17 00
0000
0006
0015
0025
0036
0000
0005
0015
0023
0033
0000
0005
0015
0025
0035
00010
WATER
TEMP
CENT
17.4
17.2
17.0
14.9
12.0
27.2
27.2
23.6
23.0
21.9
23.4
22.8
22.3
21.4
19.0
00665 32317
DATE TIME DEPTH PHOS-TOT CHLRPHYL
FROM OF A
TO UAY FEET MG/L P UG/L
73/05/10 15 50
15 50
15 50
15 50
15 50
73/08/08 12 15
13 15
12 15
12 15
12 15
17 00
17 00
17 00
17 00
17 00
73/10/10
0000
0006
0015
0025
0036
0000
0005
0015
0023
0033
0000
0005
0015
0025
0035
0.031
0.050
0.037
0.045
0.046
0.041
0.057
0.060
0.078
0.080
0.032
0.038
0.0<*0
0.087
0.268
12.5
6.0
7.2
180503
39 28 42.0 086 53 57.0 3
CATARACT LAKE
18133 INDIANA
051991
11EPALES 2111202
0040 FEET DEPTH CLASS 00
00300
DO
MG/L
10.0
8.6
8.5
9.1
9.0
0.1
0.2
0.8
7.2
2.0
0.0
0.0
00077
TRANSP
SECCHI
INCHES
60
36
48
00094
CNDUCTVY
FIELD
MICROMHO
395
380
360
400
405
260
264
230
262
260
297
293
297
333
394
00400
PH
SU
7.60
8.00
8.00
7.80
7.70
8.20
8.50
7.20
7.20
7.20
8.30
8.20
7.50
7.20
7.00
00410
T ALK
CAC03
MG/L
138
139
139
138
150
99
97
93
108
115
124
125
128
153
200
00610
NH3-N
TOTAL
MG/L
0.050
0.050
0.070
0.110
0.310
0.100
0.100
0.120
0.180
0.470
0.200
0.240
0.450
1.730
4.880
00625
TOT KJEL
N
MG/L
0.400
0.400
0.600
0.700
1.000
1.100
1.000
0.700
0.800
1.100
1.400
0.800
0.900
2.300
6.200
00630
N02&N03
N-TOTAL
MG/L
2.790
2.880
2.780
2.820
2.800
1.340
1.380
1.460
1.630
1.270
0.060
0.060
0.050
0.040
0.050
00671
PHOS-DIS
ORTHO
MG/L P
0.009
0.009
0.011
0.017
0.023
0.009
0.024
0.038
0.044
0.044
0.007
0.012
0.015
0.010
0.012
-------
APPENDIX E
TRIBUTARY and WASTEWATER
TREATMENT PLANT DATA
-------
STORET RETRIEVAL DATE 76/03/30
1805A1
39 29 15.0 086 55 30.0 4
MILL CREEK
18 7.5 POLAND
0/CATARACT LAKE 051991
BANK SAMPLE AT CAGuE MILL GAGING STATION
11EPALES 2111204
0000 FEET DEPTH CLASS 00
DATE
FROM
TO
73/06/10
73/07/09
73/08/12
73/09/23
73/10/25
73/11/27
73/12/17
74/01/16
74/02/05
74/02/20
74/03/06
74/03/20
7^/04/17
74/05/15
00630 00625
TIME DEPTH N02&N03 TOT KJEL
OF N-TOTAL N
DAY FEET
14 10
16 30
10 30
18 00
17 00
11 45
12 00
12 00
13 03
12 00
12 00
13 00
12 50
MG/L
2.040
3.0UO
1.340
0.410
0.320
0.290
2.100
3.080
2.900
2.940
2.600
2.600
2.640
1.920
MG/L
1.200
2.310
1.000
1.000
1.800
1.000
1.300
0.800
0.600
1.400
1.200
0.700
0.900
1.600
00610 00671 00665
NH3-N PHOS-DIS PHOS-TOT
TOTAL ORTHO
MG/L
0.160
0.470
0.260
0.310
0*580
0.336
0.192
0.104
0.090
0.090
0.072
0.065
0.025
0.150
MG/L P
0.007
0.015
0.032
0.018
0.005K
0.012
0.060
0.064
0.065
0.055
0.035
0.035
0.005
0.015
MG/L P
0.040
0.040
0.080
0.045
0.025
0.190
0.095
0.090
0.080
0.080
0.110
0.065
0.040
0.050
K VALUE KNOWN TO BE
LESS THAN INDICATED
-------
STORET RETRIEVAL DATE 76/03/30
1805A2
39 25 59.0 086 48 48.0 4
MILL CKtEK
Id 7.5 CATAKACT
I/CATARACT LAKE 051991
btC HO flRDG .5 N OF CATAKACT
11EPALES 2111204
0000 FEET DEPTH CLASS 00
DATE
FROM
TO
73/06/10
73/07/09
73/08/12
73/09/23
73/10/25
73/11/27
73/12/17
74/01/16
74/02/05
74/02/20
74/03/06
74/03/20
74/04/17
74/05/15
TIME DEPTH
OF
DAY FEET
13 30
16 00
09 50
17 15
16 20
11 00
11 00
11 00
11 00
11 00
11 00
11 30
11 00
00630
N02«kN03
N-TOTAL
MG/L
4.900
3.400
1.080
0.490
0.210
4.700
2.900
3.520
3.960
3.100
3.600
3.900
3.100
4.500
00625
TOT KJEL
N
MG/L
0.620
1.260
2.400
1.400
0.550
1.200
0.600
0.700
0.400
1.800
0.700
0.500
0.800
1.000
00610
NH3-N
TOTAL
MG/L
0.080
0.115
0.052
0.046
0.044
0.036
0.076
0.084
0.050
0.105
0.020
0.015
0.065
0.065
00671
PHOS-DIS
ORTHO
MG/L P
0.060
0.046
0.032
0.034
0.042
0.116
0.024
0.040
0.025
0.075
0.035
0.025
0.025
0.030
00665
PHOS-TOT
MG/L P
0.090
0.075
0.110
0.095
0.080
0.440
0.040
0.125
0.035
0.250
0.165
0.050
0.040
0.080
-------
STORET RETRIEVAL DATE 76/03/30
180581
39 30 16.0 086 48 05.0 4
DOE CKEEK
18 7.5 CLOVEROALE
T/CATARACT LAKE 051991
SEC RD BRDG AT S END OF CLOVERDALE
11EPALES 2111204
0000 FEET DEPTH CLASS 00
DATE
FROM
TO
73/06/10
73/07/09
73/08/12
73/09/23
73/10/25
73/11/27
73/12/17
74/01/16
7^/02/05
74/02/20
7W03/06
74/03/20
74/04/17
74/05/15
00630 00625
TIME DEPTH N02&N03 TOT KJEL
OF N-TOTAL N
DAY FEET
13
17
09
17
16
10
10
10
10
10
10
10
10
20
00
30
00
10
30
20
00
30
30
30
30
30
MG/L
3
3
1
2
3
4
3
2
4
2
2
3
2
1
.900
.700
.160
.400
.400
.400
.800
.760
.300
.200
.400
.000
.800
.010
MG/L
0.
1.
4.
0.
1.
0.
1.
0.
1.
1.
730
680
000
800
400
800
700
700
200
100
0.500
0.
1.
2.
600
000
700
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.
126
150
210
054
110
088
420
132
240
175
035
040
040
075
MG/L
0.
0.
0.
0.
0.
0.
0.
0.
a.
0.
0.
0.
0.
0.
p
250
280
230
650
990
116
140
060
070
060
030
032
040
030
MG/L P
0.290
0.420
0.890
0.720
1.150
0.345
0.180
0.110
0.095
0.080
0.080
0.055
0.075
-------
STORET RETRIEVAL DATE 76/03/30
180501
39 30 55.0 086 50 00.0 4
UNNAMED STREAM
18 7.5 CLOVERDALE
T/CATARACT LAKE 051991
WT 343 BRDG 1.5 MI W OF CLOVERDALE
HEPALES 2111204
0000 FEET DEPTH CLASS 00
DATE
FROM
TO
73/06/10
73/07/09
73/08/12
73/10/25
73/11/27
73/12/17
74/01/16
74/02/05
74/02/20
74/03/06
74/03/20
74/04/17
74/05/15
00630 00625
TIME DEPTH N02&N03 TOT KJEL
OF N-TOTAL N
DAY FEET
11
17
16
15
10
09
09
09
09
09
09
09
20
40
40
45
05
20
15
30
30
30
30
00
MG/L
0
0
0
0
0
0
0
0
0
0
0
0
1
.490
.390
.330
.400
.790
.510
.660
.560
.420
.300
.290
.240
.800
MG/L
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
3.
460
460
480
600
600
400
600
200
300
300
200
200
900
00610 00671 00665
NH3-N PHOS-DIS PHOS-TOT
TOTAL ORTHO
MG/L
0.
0.
0.
0.
027
042
027
022
0.044
0.
0.
0.
0.
0.
0.
0.
1.
036
072
035
030
015
030
015
200
MG/L
0.
0.
0.
0.
0.
o.
0.
0.
0.
0.
0.
0.
0.
p
010
015
008
Oil
016
008
020
010
010
010
010
005K
330
MG/L P
0.030
0.030
0.045
0.050
0.065
0.060
0.010
0.020
0.040
0.010
0.015
1.250
K VALUE KNOWN TO BE
LESS THAN INDICATED
-------
STORET RETRIEVAL DATE 76/03/30
1805E1
39 29 55.0 086 50 00.0 4
FERGUSON BRANCH
18 7.5 CLOVtROALE
T/CATARACT LAKE 051991
QNORY RU B«DG 1.25 MI M OF CLOVEROALE
11EPALES 2111204
0000 FEET DEPTH CLASS 00
DATE
FROM
TO
73/06/10
73/07/09
73/08/12
73/09/23
73/10/25
73/11/27
73/12/17
74/01/16
74/02/05
74/02/20
74/03/06
74/03/20
74/04/17
74/05/15
00630 00625
TIME DEPTH N02&N03 TOT KJEL
OF N-TOTAL N
DAY FEET
13
16
09
16
16
10
10
09
10
10
10
10
10
10
45
30
50
00
15
00
30
00
00
00
00
00
MG/L
0
0
0
0
0
0
0
0
0
0
0
0
0
0
.530
.400
.570
.046
.039
.690
.540
.830
.810
.650
.528
.588
.352
.360
MG/L
0
0
0
0
0
0
1
0
0
0
0
0
1
1
.330
.480
.350
.230
.450
.800
.000
.800
.200
.500
.300
.600
.600
.600
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.
031
037
075
022
018
040
052
068
020
030
025
040
035
020
MG/L
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
p
014
Oil
014
014
014
020
005K
028
015
010
010
010
005
025
MG/L P
0.035
0.020
0.035
0.035
0.195
0.015
0.070
0.015
0.025
0.050
0.015
0.015
K VALUE KNOWN TO BE
LESS THAN INDICATED
-------
STORE! RETRIEVAL DATE 76/03/30
1805E2
39 30 30.0 086 49 30.0
FERGUSON CREEK
18 7.5 CATARACT
T/CATARACT LAKE
QNOKY RO BHOG 2.5 MI WSW OF CLOVEROALE
11EPALES 2111204
0000 FEET DEPTH CLASS 00
051991
DATE
FROM
TO
73/06/10
73/07/09
73/08/12
73/09/23
73/10/25
73/11/27
73/12/17
74/01/16
74/02/05
74/02/20
74/03/06
74/03/20
74/04/17
74/05/15
00630 00625
TIME DEPTH N02^N03 TOT KJEL
OF N-TOTAL N
DAY FEET
11
17
09
16
15
10
09
09
09
09
09
09
09
25
30
10
30
55
00
00
00
00
00
00
00
30
MG/L
0
0
0
0
0
0
0
1
3
.450
.340
.430
.198
.180
.672
.640
.850
.700
2.500
2
3
3
0
.940
.200
.080
.184
MG/L
0.
?.
?.
0.
0.
310
100
700
290
850
1.000
0.
4.
2.
2.
1.
1.
3.
1.
500
200
100
000
400
500
800
900
00610 00671 00665
NH3-N PHOS-DIS PHOS-TOT
TOTAL ORTHO
MG/L
0.
n.
0.
0.
0.
0.
0.
1.
0.
0.
0.
0.
1.
0.
038
069
069
025
022
026
052
500
830
540
290
420
400
035
MG/L
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
P
010
012
005K
010
012
023
008
400
330
240
155
190
0.440
MG/L P
0.030
0.020
0.025
0.025
0.180
0.030
0.760
0.450
0.330
0.310
0.280
0.550
0.380
K VALUE KNOWN TO BE
LESS THAN INDICATED
-------
STORE! RETRIEVAL DATE 76/03/30
1805CA AS1805CA P001000
39 30 45.0 086 48 07.0 4
CLOVERDALE
18 7.5 CLOVEROALE
T/CATARACT LAKE 051991
RABBIT RUN/DOE CREEK
11EPALES 2141204
0000 FEET DEPTH CLASS 00
DATE
FROM
TO
73/06/01
73/07/02
73/08/01
73/09/01
73/10/01
73/11/05
73/12/07
74/01/10
74/02/06
74/03/06
74/04/04
74/05/09
74/06/04
00630
TIME DEPTH N02*N03
OF N-TOTAL
DA* FF.ET
09
09
09
09
09
09
10
09
10
08
09
09
09
00
00
00
00
00
00
00
30
20
45
00
00
30
MG/L
0
0
0
0
0
0
0
0
0
0
0
0
.240
.130
.130
.021
.040
.340
.120
.160
.040
.400
.360
.360
00625
TOT KJEL
N
MG/L
45.000
32.800
19.800
39.000
37.800
43.500
21.000
22.000
20.000
9.000
10.000
26.000
29.000
00610 00671
NH3-N PHOS-DIS
TOTAL ORTHO
MG/L
0.160
9.000
1.100
10.600
16.000
2.300
6.160
4.200
0.100
0.370
6.600
7.000
MG/L P
6.000
3.575
2.200
4.600
3.700
3.600
2.700
3.400
3.600
1.500
1.550
3.300
5.250
00665
PHOS-TOT
50051 50053
FLOW CONDUIT
RATE FLOW-MGU
MG/L P INST
12.000
5.250
4.300
7.870
10.500
11.500
4.700
5.500
5.500
2.200
2.800
6.400
7.800
0
0
0
0
0
0
0
0
0
0
0
0
0
MOD MONTHLY
.062
.062
.062
.062
.062
.090
.099
.066
.066
.067
.075
.071
.091
0.062
0.062
0.062
0.062
0.062
0.085
0.069
0.066
0.069
0.068
0.072
0.075
0.080
------- |