U.S. ENVIRONMENTAL PROTECTION AGENCY
NATIONAL EUTROPHICATION SURVEY
WORKING PAPER SERIES
REPORT
ON
MORSE RESERVOIR
HAMILTON COUNT/
INDIANA
EPA REGION V
WORKING PAPER No, 337
CORVALLIS ENVIRONMENTAL RESEARCH LABORATORY - CORVALLIS, OREGON
and
ENVIRONMENTAL MONITORING & SUPPORT LABORATORY - LAS VEGAS, NEVADA
699-440
-------
REPORT
ON
MORSE RESERVOIR
HAMILTON COUNTY
INDIANA
EPA EG ION V
WORKING PAPER No, 337
WITH THE COOPERATION OF THE
INDIANA STATE BOARD OF HEALTH
AND THE
INDIANA NATIONAL GUARD
APRIL, 1976
-------
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 Sumnary 5
IV. Nutrient Loadings 9
V. Literature Reviewed 14
VI. Appendices 15
-------
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.
-------
m
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 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.
-------
iv
NATIONAL EUTROPHICATION SURVEY
STUDY LAKES
STATE OF INDIANA
LAKE NAME
Bass
Cataract
Crooked
Dallas
Geist
Hami 1 ton
Hovey
James
James
Long
Marsh
Mississinewa
Maxinkuckee
Monroe
Morse
01 in
01i ver
Pi geon
Syl van
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
Hami1 ton
LaGrange
LaGrange
Steuben
Noble
Kosciusko
Ripley
Kosciusko
Kosciusko
LaGrange
Union
Kosciusko
LaGrange
-------
86'10
86'00
MORSE RESERVOIR
® Tributary Sampling Site
X Lake Sampling Site
fP Sewage Treatment Facility
X7 Drainage Area Boundary
I 1 rJ L, 1 ,J , 1
o o •, 5 Mi.
Scale _____
4020—
Ind.
Ls
Map Location
NOBLESVILLE
4010—
-------
MORSE RESERVOIR
STORE! NO. 1829
I. CONCLUSIONS
A. Trophic Condition:
Survey data indicate that Morse Reservoir is eutrophic. It
ranked twenty-fifth in overall trophic quality when the 27 Indiana
lakes sampled in 1973 were compared using a combination of six
parameters*. Twenty of the lakes had less and one had the same
median total phosphorus, ten had less and one had the same median
dissolved phosphorus, all of the other lakes had less median inor-
ganic nitrogen, 25 had less mean chlorophyll a^, and 23 had greater
mean Secchi disc transparency. Marked depression of hypolimnetic
dissolved oxygen occurred at both sampling stations in August, and
oxygen was depleted at station 1 in October.
Survey limnologists observed submerged and emergent macrophytes
at various locations in the reservoir.
B. Rate-Limiting Nutrient:
The algal assay results indicate that Morse Reservoir was lim-
ited by phosphorus at the time the sample was collected (05/10/73).
The reservoir data indicate phosphorus limitation in August and
October as well.
C. Nutrient Controllability:
1. Point sources—Point-source phosphorus contributions ac-
counted for 32% of the total input to Morse Reservoir during the
See Appendix A.
-------
2
sampling year. The wastewater treatment plant at Tipton con-
tributed 25.3% of the total, and the remaining four plants at
Atlanta, Arcadia, Cicero, and Sheridan collectively contributed
6.6%.
The present loading of 6.52 g/m2/yr is over five times that
proposed by Vollenweider (Vollenweider and Dillon, 1974) as a
eutrophic loading (see page 13). However, the mean hudraulic
retention time of the reservoir is a relatively short 56 days,
and Vollenweider's model may not apply.
While even complete removal of phosphorus at the listed point
sources would still leave a loading of 4.4 g/m2/yr, i-n view of the
questionable applicability of Vollenweider's model and the phos-
phorus-limited condition of the reservoir, it is likely that a
high degree of phosphorus removal at the significant point sources
would result in improvement in the trophic condition of the reser-
voir.
2. Non-point sources—It is calculated that non-point sources
contributed 68.0% of the total phosphorus load during the sampling
year. Cicero Creek contributed 52.4%, Little Cicero Creek con-
tributed 9.3%, and Hinkle Creek contributed 3.5%. Ungaged tribu-
taries were estimated to have contributed 2.6% of the total.
Cicero Creek had a phosphorus export rate of 55 kg/km2 during
the sampling year. This rate is high compared to the rates of the
-------
3
other tributaries of the reservoir (see page 12). A number of
small towns in the Cicero Creek drainage do not have waste treat-
ment facilities and are served by septic tanks (BonHomme, 1976).
These include East Union, Goldsmith, Hobbs, Millersburg, and
Tetersburg. It is possible that septic tank drainage from these
communities, along with urban drainage from the City of Tipton,
account for the higher Cicero Creek phosphorus export rate.
-------
II. LAKE AND DRAINAGE BASIN CHARACTERISTICS1"
A. Lake Morphometry :
1. Surface area: 5.57 kilometers2.
2. Mean depth: 4.7 meters.
3. Maximum depth: 15.2 meters.
4. Volume: 26.179 x 106 m3.
5. Mean hydraulic retention time: 56 days (based on outflow).
B. Tributary and Outlet:
(See Appendix C for flow data)
1. Tributaries -
Drainage Mean flow
Name area (km2)* (m3/sec)*
Cicero Creek 348.4 3.37
Hinkle Creek 52.1 0.58
Little Cicero Creek 112.1 1.15
Minor tributaries &
immediate drainage - 37.1 0.35
Totals 549.7 5.45
2. Outlet -
Cicero Creek 555.3** 5.43
C. Precipitation***:
1. Year of sampling: 122.0 centimeters.
2. Mean annual: 100.8 centimeters.
t Table of metric conversions—Appendix B.
tt McCollam, 1975.
* For limits of accuracy, see Working Paper No. 175, "...Survey Methods,
1973-1976".
** Includes area of lake.
*** See Working Paper No. 175.
-------
5
III. LAKE WATER QUALITY SUMMARY
Morse 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 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 phyto-
plankton 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 ^analysis. The maximum
depths sampled were 9.8 meters at station 1, 6.1 meters at station
2, and 3.4 meters at station 3.
The sampling results are presented in full in Appendix D and
are summarized in the following table.
-------
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 ( 5/10/73)
3 SITES
CHEMICAL CHARACTERISTICS FOR
STORET CODE 1829
MORSE RESERVOIR
2ND SAMPLING ( 8/ 2/73)
3 SITES
3RD SAMPLING (10/15/73)
3 SITES
RANGE
14.6
8.3
510.
8.2
174.
0.055
0.006
5.070
0.030
0.500
5.120
5.970
23.4
0.5
- 18.8
- 12.2
- 590.
8.7
- 208.
- 0.274
- 0.035
- 6.390
- 0.120
- 0.900
- 6.450
- 6.890
- 67.2
0.9
MEAN
16.6
10.2
532.
8.4
184.
0.097
0.019
5.858
0.065
0.609
5.923
6.467
39.5
0.8
MEDIAN
16.3
10.3
520.
8.5
177.
0.082
0.015
6.000
0.050
0.500
6.050
6.500
28.0
0.9
RANGE
14.7
0.7
3BO.
7.4
116.
0.029
0.004
1.290
0.050
1.400
1.400
3.890
48.2
0.4
- 26.6
- 12.5
- 437.
9.0
- 197.
- 0.210
- 0.018
- 3.540
- 1.560
- 2.900
- 3.600
- 5.300
- 103.4
0.9
MEAN
24.3
7.2
394.
8.5
136.
0.070
0.008
2.572
0.420
2.067
2.992
4.639
68.4
0.7
MEDIAN
25.8
9.7
387.
8.8
121.
0.044
0.006
2.960
0.070
1.900
3.170
4.850
53.5
0.8
RANGE
16.5
0.0
328.
7.3
136.
0.043
0.003
0.100
0.070
1.200
1.020
1.870
20.2
0.4
- 20.7
9.8
- 434.
8.6
- 285.
- 0.279
- 0.022
- 1.720
- 4.090
- 6.700
- 4.190
- 6.800
- 107.7
0.8
MEAN
19.8
5.2
365.
8.0
163.
0.119
0.009
0.921
0.664
1.992
1.S8S
2.912
60.6
0.6
MEDIAN
20.1
6.0
344.
8.1
142.
0.098
0.008
0.910
0.145
1.300
1.075
2.610
53.9
0.6
-------
B. Biological characteristics:
1. Phytoplankton -
Sampling
Date
05/10/73
08/02/73
10/15/73
2. Chlorophyll a_ -
Sampling
Date
05/10/73
08/02/73
10/15/73
Dominant
Genera
1.
2.
3.
4.
5.
1.
2.
3.
4.
5.
1.
2.
3.
4.
5.
Melosira sp.
Stejshanodiscus sj3.
Chlamydomonas sp.
Dactyl ococcops is sp
Cryptomonas sp.
Other genera
Total
Raphidiopsis sjj.
Oscillatoria sj>.
Lyngbya sp_.
Microcystis sp.
Merismopedia SJD.
Other genera
Total
Oscillatoria sp.
Raphidiopsis SJD.
StejDhanodiscus sp.
Lyngbya sp.
Merismojjedia sp.
Other genera
Total
Station
Number
1
2
3
1
2
3
1
2
3
Algal Units
per ml
7,
2,
1,
976
705
554
863
403
3,534
17,035
56,584
27,006
,429
,144
3.
3,
2.
143
5,716
98,022
8,377
3,064
2,298
1,484
1,197
5.313
21,733
Chlorophyll
(yg/D
23.4
28.0
67.2
48
53
103
20
53
,2
,5
,4
.2
,9
107.7
-------
8
Limiting Nutrient Study:
1. Filtered, and nutrient spiked -
Ortho P Inorganic N Maximum yield
Spike (mg/1) Cone, (mg/1) Cone, (mg/1) (mg/1-dry wt.)
Control 0.015 4.980 2.5
0.050 P 0.065 4.980 20.2
0.050 P + 1.0 N 0.065 5.980 27.6
1.0 N 0.015 5.980 2.7
2. Discussion -
The control yield of the assay alga, Selenastrum capri-
cornutum, indicates that the potential primary productivity
of Morse Reservoir was moderately high at the time the sample
was taken (05/10/73). Also, an eight-fold increase in yield
with the addition of only orthophosphorus indicates phosphorus
limitation at that time. Note that the addition of only nitro-
gen resulted in a yield which was not significantly greater
than that of the control.
The reservoir data also indicate phosphorus limitation;
i.e., the mean inorganic nitrogen/orthophosphorus ratios were
176/1 or greater at all sampling times.
-------
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 Indian District Office of the U.S. Geological Survey for the
tributary sites nearest the reservoir.
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
at station B-l, in kg/km2/year, and multiplying by the ZZ area in km2.
The operators of the Arcadia, Tipton, Sheridan, and Cicero waste-
water treatment plants provided monthly effluent samples and corresponding
flow data. The Atlanta stabilization ponds did not overflow during the
sampling year but were drawn down in October; the operator provided
samples during the two-day drawdown.
See Working Paper No. 175.
-------
10
The estimated phosphorus load from septic tanks was reduced by
50% to adjust for the ban on phosphate detergents that has been in
effect .in Indiana since 1972.
A. Waste Sources:
1. Known municipal -
Name
Arcadia
Atlanta
Tipton
Cicero
Sheridan
Pop.
Served
1,338
700
5,500
1,450
2,000
Mean Flow
Treatment (m3/d)
tr. filter 824.0
stab, ponds 79.5
(two days)
tr. filter 5,579.1
act. sludge 690.8*
+ pond
act. sludge 1,213.1
Receiving
Water
Cicero Creek
Cicero Creek
Cicero Creek
Morse Reservoir
Symons Ditch/
Little Cicero
Creek
2. Known industrial - A small vegetable canning plant is located
north of Tipton; however, it is not believed to be of nutrient
significance (BonHomme, 1976).
t Treatment plant questionnaires.
* A recent survey of the Cicero plant revealed the flow meter was recording
only 55% of the actual flow (BonHomme, op. cit.); nutrient loads attributed
to this source have been adjusted accordingly.
-------
11
B. Annual Total Phosphorus Loading - Average Year:
1. Inputs -
kg P/ % of
Source yr total
a. Tributaries (non-point load) -
Cicero Creek 19,010 52.4
Hinkle Creek 1,280 3.5
Little Cicero Creek 3,375 9.3
b. Minor tributaries & immediate
drainage (non-point load) - 930 2.6
c. Known municipal STP's -
Arcadia 840 2.3
Atlanta 45 0.1
Tipton 9,190 25.3
Cicero 865 2.4
Sheridan 660 1.8
d. Septic tanks* - 5 <0.1
e. Known industrial - None
f. Direct precipitation** - 95_ 0.3
Total 36,295 100.0
2. Outputs -
Lake outlet - Cicero Creek 17,260
3. Net annual P accumulation - 19,035 kg.
* Estimate based on 21 lakeshore dwellings; see Working Paper No. 175.
** See Working Paper No. 175.
-------
12
Annual Total Nitrogen Loading - Average Year:
1. Inputs -
kg N/ % of
Source y_r total
a. Tributaries (non-point load) -
Cicero Creek 556,440 63.3
Hinkle Creek 69,100 7.9
Little Cicero Creek 170,405 19.4
b. Minor tributaries & immediate
drainage (non-point load) - 50,085 5.7
c. Known municipal STP's -
Arcadia 4,140 0.5
Atlanta 105 <0.1
Tipton 16,150 1.8
Cicero 2,295 0.3
Sheridan 3,980 0.4
d. Septic tanks* - 225 <0.1
e. Known industrial - None
f. Direct precipitation** - 6,015 0.7
Total 878,940 100.0
2. Outputs -
Lake outlet - Cicero Creek 786,085
3. Net annual N accumulation - 92,855 kg.
Mean Annual Non-point Nutrient Export by Subdrainage Area:
Tributary kg P/km2/yr kg N/km2/yr
Cicero Creek 55 1,597
Hinkle Creek 25 1,326
Little Cicero Creek 30 1,520
* Estimate based on 21 lakeshore dwellings; see Working Paper No. 175.
** See Working Paper No. 175.
-------
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 Accumul ated
grams/mVyr 6.52 3.42 157.8 16.7
Vollenweider phosphorus loadings
(g/m2/yr) based on mean depth and mean
hydraulic retention time of Morse Reservoir:
"Dangerous" (eutrophic loading) 1.16
"Permissible" (oligotrophic loading) 0.58
-------
14
V. LITERATURE REVIEWED
BonHomme, Harold L., 1976. Personal communication (review of pre-
liminary report). IN Div. of Water Poll. Contr., Indianapolis,
McCollam, Archie, 1975. Personal communication (lake morphometry).
U.S. Geol. Surv., Indianapolis.
Vollenweider, R. A., and P. 0. Dillon, 1974. The application of
the phosphorus loading concept to eutrophication research.
Natl. Res. Council of Canada Pub!. No. 13690, Canada Centre
for Inland Waters, Burlington, Ontario.
-------
VI. APPENDICES
APPENDIX A
LAKE RANKINGS
-------
LAKE DATA TO BE USED IN RANKINGS
LAKE
CODE
180b
181)
1817
1827
iaan
1829
183b
1837
1839
1840
18i>l
1842
18*3
1844
1845
1846
1*47
1648
1849
1850
1851
.852
1853
1654
1R55
1856
1857
LAKE NAME
CATARACT LAKE
GEIST RESERVOIR
JAMES LAKE
MISS1SSINEWA RESERVOIR
MONROE RESERVOIR
MORSE RESERVOIR
WAWASFE LAKE
WE8STER 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
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
.823
.222
.500
.000
.167
.667
.125
.333
.400
.500
.333
.333
.000
.833
.333
.000
.375
.111
.444
.667
.067
.333
.167
MEAN
CHLOHA
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 DO
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
.000
.000
.000
.000
.000
.000
.000
.000
.900
.800
.800
.600
.500
.000
.000
.000
.000
.000
.000
.000
MEDIAN
DISS OrfTnO H
o.ou
0.009
O.OOd
0.029
0.00'
0.009
0.003
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 WITH HIGHER VALUES (NUMBER OF LAKES WITH HIGHE* VALUES)
LAKE
CODE
1HOS
1811
1817
1827
1828
1839
1836
1837
1839
1840
1841
1842
1843
1844
18<>5
18*6
1847
1848
1849
1850
1851
1852
1853
1854
1855
1856
1857
LAKE NAME
CATARACT LAKE
GEIST RESERVOIR
JAMES LAKE
MISSISSINEWA RESERVOIR
MONROE RESERVOIR
MORSE RESERVOIR
WAWASEE LAKE
WEBSTER LAKE
WHITEWATER LAKE
W I NONA 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
MAKSH LAKE
HAMILTON LAKE
MEDIAN
TOTAL f
37 (
27 (
73 (
12 (
67 (
?3 (
94 (
67 (
19 (
SO (
50 (
50 (
77 (
85 (
62 <
94 (
100 <
4 (
31 (
8 (
42 <
81 (
88 (
0 (
37 (
15 (
58 (
9)
7)
19)
3)
17)
6)
24)
17)
5)
12)
12)
12)
20)
22)
16)
24)
26)
1)
8)
2)
11)
21)
23)
0)
9)
4)
15)
MEDIAN
INORIJ N
15
35
42
4
69
0
85
62
19
27
54
50
81
88
58
23
46
96
38
31
77
100
92
12
8
73
65
( 41
( 9)
1 11)
< 1)
I 18)
( 0)
( 22)
( 16)
( 5)
( 7)
( 14)
( 13)
( 21)
( 23)
I 15)
( 6)
( 12)
( 25)
( 10)
( 8)
( 20)
( 261
( 24)
( 3)
( 2)
( 19)
< 17)
500-
MEAN SEC
31
15
S8
8
54
12
96
62
23
38
65
50
85
92
69
81
88
27
0
4
19
77
100
44
44
35
73
( d)
( 4)
( 15)
( 2)
I 14)
( 3)
( 25)
( 16)
( 6)
( 10)
< 17)
( 13)
< 22)
( 24)
( IB)
( 21)
( 23)
( 7)
( 0)
( 1)
( 5)
I 20)
( 26)
( 11)
( 11)
( 9)
( 19)
MEAN
C1LORA
62 (
12 1
50 (
38 (
71 (
4 I
88 (
54 I
19 (
58 (
65 (
42 (
85 I
77 <
69 (
92 (
100 (
8 1
0 <
27 (
23 (
81 1
96 (
35 (
46 (
15 (
31 (
16)
3)
13)
10)
19)
1)
23)
14)
5)
15)
17)
ID
22)
20)
18)
24)
26)
2)
0)
7)
6)
21)
25)
9)
12)
4)
8)
15-
MIN 00
35
92
35
35
35
35
as
35
35
35
35
35
35
35
35
73
79
79
96
88
100
35
35
35
35
35
35
( 0)
( 24)
( 0)
( 0)
( 0)
( 0)
( 22)
I 0)
( 0)
( 0)
( 0)
I 0)
( 0)
< 0)
( 0)
( 19)
( 20)
( 20)
( 25)
( 23)
( 26)
( 0)
( 0)
( 0)
( 0)
I 0)
( 0)
MEDIAN
DISS ORTHO P
37 (
62 (
65 (
8 (
69 (
58 (
98 (
81 (
42 (
52 (
37 (
52 (
98 <
85 (
31 (
92 (
88 I
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)
71
1)
5)
INJEX
NO
an
243
323
105
367
132
546
3bl
157
260
3U6
279
461
462
324
455
501
237
177
173
307
449
48b
126
14f
177
231
-------
LAKES RANKED BY INDEX NOS.
RANK LAKE CODE LAKE NAME INDEX NO
1 1636 wAWASEE LAKE 546
2 18*7 OLIVER LAKE 501
3 1853 LAKE JAMES 486
4 1844 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 324
11 1817 JAMES LAKE 323
12 1851 BASS LAKE 307
13 1841 XESTLER 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 HOVEY 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
03/29/76
LAKE CODE 1829
MORSE RESERVOIR
TOTAL DRAINAGE AREA OF LAKE(SO KM)
SUB-DRAINAGE
TRIBUTARY AREA(SO KM)
JAN
FEB
555.3
MAR
NORMALIZED FLOWS(CMS)
APR MAY JUN JUL AUG SEP
OCT
NOV
DEC
MEAN
1829A1
1829A2
1829BI
1829C1
1829ZZ
558.1
348.4
52.1
112.1
37.3
5.97
3.85
0.697
1.25
0.442
7.73
4.93
0.912
1.63
0.535
10.34
6.43
1.048
2.02
0.765
11.33
6.34
1.161
2.11
0.711
5.32
3.48
0.592
1.13
0.459
5.69
3.54
0.677
1.32
0.351
3.51
2.63
0.385
1.08
0.210
1.83
0.92
0.193
0.46
0.071
1.03
0.69
0.082
0.18
0.068
2.17
1.42
0.170
0.39
0.071
4.19
2.74
0.422
0.94
0.181
6.34
3.65
0.626
1.32
0.340
5.43
3.37
0.577
1.15
0.349
SUMMARY
TOTAL DRAINAGE AREA OF LAKE
SUM OF SUB-DRAINAGE AREAS
MEAN MONTHLY FLOWS AND DAILY FLOWS(CMS)
555.3
549.9
TOTAL FLOW IN = 65.63
TOTAL FLOW OUT » 65.45
TRIBUTARY MONTH YEAR
1829A1
MEAN FLOW DAY
FLOW DAY
FLOW DAY
FLOW
1829A2
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
8.467
1.189
8.014
0.906
3.002
11.270
15.971
26.108
10.449
11.836
14.102
4.984
4.474
0.708
4.984
0.481
1.218
7.589
9.996
16.905
6.796
6.938
6.796
8.891
9
7
12
9
15
10
9
13
9
10
9
18
9
7
12
9
15
10
9
13
9
10
9
18
10.024
1.359
15.433
0.311
1.812
0.821
6.570
3.540
7.391 24
7.759 17
23.531
2.152
4.757
0.765
13.649
0.198
0.906
0.680
4.446
4.078
4.502 24
4.163 17
16.112
15.065
17.500
5.975
9.628
2.577
-------
TRIBUTARY FLOW INFORMATION FOR INDIANA
03/29/76
LAKE CODE 1829
MORSE RESERVOIR
MEAN MONTHLY FLOWS AND DAILY FLOWS(CMS)
TRIBUTARY MONTH YEAR
1829B1
1829CI
1829ZZ
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
MEAN FLOW DAY
1.246
0.176
0.680
0.144
0.595
1.133
1.529
2.492
1.019
1.501
1.331
1.444
1.784
0.249
1.246
0.187
1.076
2.492
3.313
4.729
1.841
2.718
2.492
3.030
0.906
0.125
0.048
0.102
0.425
0.793
0.110
1.784
0.736
1.076
0.963
1.019
9
7
12
9
15
10
9
13
9
10
9
18
9
7
12
9
15
10
9
13
9
10
9
18
9
7
12
9
15
10
9
13
9
10
9
18
FLOW DAY
FLOW DAY
FLOW
0.708
0.170
4.842
0.074
0.204
0.119
0.368
0.453
0.680
0.708
2.917
4.219
1.388
0.252
4.361
0.028
0.510
0.340
1.161
0.736
1.104
1.359
5.663
5.125
0.510
0.122
3.455
0.054
0.340
0.085
0.263
0.040
0.538
0.538
0.210
3.002
24
17
24
17
24
17
1.104
0.850
2.322
1.218
0.821
0.651
-------
APPENDIX D
PHYSICAL and CHEMICAL DATA
-------
STORE! RETRIEVAL DATE 76/03/30
DATE
FROM
TO
73/05/10
73/08/02
73/10/15
DATE
FROM
TO
73/05/10
73/08/02
73/10/15
TIME DEPTH
OF
DAY FEET
12 22 0000
12 22 0009
12 22 0015
12 22 0032
15 30 0000
15 30 0005
15 30 0015
15 30 0030
11 00 0000
11 00 0005
11 00 0015
11 00 0025
11 00 0031
TIME DEPTH
OF
DAY FEET
12 22 0000
12 22 0009
12 22 0015
12 22 0032
15 30 0000
15 30 0005
15 30 0015
15 30 0030
11 00 0000
11 00 0005
11 00 0015
11 00 0025
11 00 0031
00010
HATER
TEMP
CENT
16.4
16.3
15.7
14.6
26.0
25.9
25.5
14.7
20.2
20.2
20.0
19.3
16.5
00665
PHOS-TOT
MG/L P
0.055
0.066
* 0.060
0.073
0.036
0.033
0.029
0.031
0.043
0.054
0.058
0.111
0.279
00300
DO
MG/L
11.3
10.3
8.3
10.6
9.7
0.7
4.6
4.0
0.0
0.0
32217
CHLRPHYL
A
UG/L
23.4
48.2
20.2
00077
TRANSP a
SECCHI FIELD
INCHES M]
36
30
30
182901
40 04 25.0 086 03 00.0 3
MORSE RESERVOIR
18057 INDIANA
051991
11EPALES 2111202
0036 FEET DEPTH CLASS 00
194
:TVY
i
IMHO
510
510
520
525
380
380
380
400
328
329
329
370
434
00400
PH
SU
8.50
8.50
8.30
8.30
8.90
8.90
8.70
7.50
7.90
7.80
7.70
7.40
7.30
00410
T ALK
CAC03
MG/L
175
176
174
177
118
117
116
197
136
137
136
179
285
00610
NH3-N
TOTAL
MG/L
0.040
0.040
0.030
0.110
0.060
0.060
0.050
1.460
0.350
0.360
0.400
1.980
4.090
00625
TOT KJEL
N
MG/L
0.500
0.500
0.500
0.500
1.800
1.500
1.400
2.300
1.200
1.300
1.200
3.300
6.700
00630
N024N03
N-TOTAL
MG/L
5.710
5.900
6.020
6.000
3.500
3.540
3.S40
2.020
0.670
0.680
. 0.670
0.190
0.100
00671
PHOS-DIS
ORTHO
MG/L P
0.007
0.006
0.006
0.015
0.007
0.006
0.005
0.004
0.009
0.006
0.007
0.018
0.022
-------
STORE! RETRIEVAL DATE 76/03/30
182903
40 05 58.0 086 02 27.0 3
MORSE RESERVOIR
18057 INDIANA
051991
DATE
FROM
TO
73/05/10
73/08/02
73/10/15
DATE
FROM
TO
73/05/10
73/08/02
73/10/15
TIME DEPTH
OF
DAY FEET
12 55 0000
12 55 0009
12 55 0015
12 55 0020
16 00 0000
16 00 0005
16 00 0019
11 25 0000
11 25 0005
11 25 0010
11 25 0015
TIME DEPTH
OF
DAY FEET
12 55 0000
12 55 0009
12 55 0015
12 55 0020
16 00 0000
16 00 0005
16 00 0019
11 25 0000
11 25 0005
11 25 0010
11 25 0015
00010
WATER
TEMP
CENT
17.0
16.3
16.1
15.4
26.4
25.8
22.2
20.7
20.5
20. S
20.5
00665
PHOS-TOT
MG/L P
0.068
0.082
0.090
0.096
0.052
0.044
0.069
0.103
0.094
0.090
0.090
00300
DO
MG/L
10.5
9.8
8.6
10.1
0.7
6.0
6.4
6.6
32217
CHLRPHYL
A
UG/L
28.0
53.5
53.9
00077 00094
TRANSP CNDUCTVY
SECCHI FIELD
INCHES MICROMHO
36 510
510
520
520
35 387
384
437
24 341
345
343
342
11EPALES 2111202
0023 FEET DEPTH CLASS 00
00400 00410 00610 00625
PH T ALK NH3-N TOT KJEL
SU
8.70
8.50
8.20
8.50
9.00
8.80
7.40
8.20
8.10
8.10
8.10
CAC03
MG/L
175
183
181
177
121
120
181
140
142
141
141
TOTAL
MG/L
0
0
0
0
0
0
1
0
0
0
0
.040
.040
.060
.100
.070
.060
.560
.130
.140
.140
.150
N
MG/L
0.600
0.500
0.500
0.600
1.900
1.800
2.900
2.100
1.400
1.300
1.200
00630
N02&N03
N-TOTAL
MG/L
6.020
6.320
. 6.390
6.270
2.960
3.050
1.610
0.930
0.910
0.910
0.930
00671
PHOS-DIS
ORTHO
MG/L P
0.014
0.022
0.033
0.033
0.006
O.OOS
0.011
0.006
0.004
0.003
0.003
-------
STORE! RETRIEVAL DATE 76/03/30
183903
40 07 58.0 086 01 28.0 3
MORSE RESERVOIR
18057 INDIANA
051991
DATE
FROM
TO
73/05/10
73/08/02
73/10/15
DATE
FROM
TO
73/05/10
73/08/02
73/10/15
TIME DEPTH
OF
DAY FEET
13 20 0000
13 20 0005
13 20 0011
16 20 0000
16 20 0009
11 45 0000
11 45 0005
11 45 0008
TIME DEPTH
OF
DAY FEET
13 20 0000
13 20 0005
13 20 0011
16 20 0000
16 20 0009
11 45 0000
11 45 0005
11 45 0008
00010
WATER
TEMP
CENT
18.8
18.1
17.5
26.6
25.6
19.9
19.5
19.6
00665
PHOS-TOT
MG/L P
0.086
0.274
0.120
0.210
0.130
0.182
0.162
0.162
00300
DO
MG/L
12.
10.
12.
6.
9.
9.
32217
00077 00094
TRANSP CNDUCTVY
SECCHI FIELD
INCHES MICROMHO
2
4
5
3
6
8
20 560
580
590
14 400
400
16 400
408
406
11EPALES 2111202
0014 FEET DEPTH CLASS 00
00400 00410 00610 00625 00630 00671
PH T ALK NH3-N TOT KJEL N02&N03 PHOS-DIS
CAC03 TOTAL N N-TOTAL ORTHO
su
8.60
8.30
8.20
9.00
8.30
8.60
8.40
8.40
MG/L
193
200
208
127
129
173
175
176
MG/L
0.050
0.080
0.120
0.110
0.350
0.070
0.080
0.080
MG/L
0.900
0.700
0.900
2.600
2.400
1.700
1.200
1.300
MG/L
5.070
5.350
5.390
1.290
1.640
1.630
1.710
1.720
MG/L P
0.015
0.022
0.035
0.018
0.014
0.010
0.011
0.010
CHLRPHYL
A
UG/L
67.
103.
107.
2
4
7
-------
APPENDIX E
TRIBUTARY and WASTEWATER
TREATMENT PLANT DATA
-------
STORE! RETRIEVAL DATE 76/03/30
1829A1
40 03 20.0 086 02 30.0 4
CICERO CREEK
18 7.5 NOBLESVILLE
0/MORSE WES 051991
HWY 38 BRDG 1 MI Nw OF JCT WITH HWY 32
11EPALES 2111204
0000 FEET DEPTH CLASS 00
DATE
FROM
TO
73/06/09
73/07/07
73/08/12
73/09/09
73/10/15
73/11/10
73/12/09
74/01/13
74/02/09
74/02/24
74/03/10
74/03/17
74/04/09
74/05/18
00630 00625
TIME DEPTH N02&N03 TOT KJEL
OF N-TOTAL N
DAY FEET
13
11
09
13
11
14
13
07
09
10
09
09
08
17
00
10
15
00
00
09
35
45
00
15
15
10
MG/L
4
4
2
0
0
0
4
4
3
4
4
4
4
5
.300
.500
.300
.600
.670
.960
.400
.800
.700
.100
.700
.400
.700
.280
MG/L
0.
1.
0.
1.
1.
1.
1.
0.
0.
0.
0.
1.
4.
1.
820
050
100K
150
130
000
100
700
600
700
800
000
500
100
00610 00671 00665
NH3-N PHOS-DIS PHOS-TOT
TOTAL ORTHO
MG/L
0.
0.
0.
o.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
027
054
021
046
198
232
104
056
077
095
095
090
175
070
MG/L
0.
0.
0.
p
006
010
005K
0.007
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
006
005K
096
136
097
080
075
070
100
015
MG/L P
0.055
0.050
0.050
0.050
0.045
0.040
0.135
0.195
0.165
0.145
0.115
0.115
0.138
0.105
K VALUE KNOWN TO BE
LESS THAN INDICATED
-------
STORET RETRIEVAL DATE 76/03/30
1829A2
40 10 30.0 086 00 01.0 4
CICEHO CREEK
18 7.5 ARCADIA
I/MORSE RES
MT PLEASANT RD BRDG .1
11EPALES
051991
M S OF E 266 ST
2111204
0000 FEET DEPTH CLASS 00
DATE
FROM
TO
73/06/09
73/07/07
73/08/12
73/09/09
73/10/15
73/11/10
73/12/09
74/01/13
74/02/09
74/02/24
74/03/10
7^/03/17
74/04/09
74/05/18
00630 00625
TIME DEPTH N02&N03 TOT KJEL
OF N-TOTAL N
DAY FEET
13
12
10
14
13
14
13
09
10
11
10
10
08
50
30
00
00
00
40
45
00
55
30
15
15
45
MG/L
9
3
2
1
1
3
5
6
5
4
6
5
6
5
.000
.500
.700
.160
.660
.200
.700
.100
.040
.100
.600
.880
.000
.010
MG/L
0.
0.
0.
1.
0.
0.
0.
0.
0.
0.
0.
1.
1.
1.
840
920
520
000
800
300
800
500
600
800
800
200
100
100
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.
086
150
420
105
025
016
056
128
085
110
065
075
055
055
MG/L
0.
0.
0.
0.
0.
0.
0.
0.
0.
P
105
118
290
810
032
320
120
105
080
0.075
0.
0.
0.
080
080
015
MG/L P
0.190
0.175
0.970
0.910
0.055
0.320
0.110
0.145
0.135
0.145
0.125
0.150
0.170
0.100
-------
STORE! RETRIEVAL DATE 76/03/30
182981
40 06 02.0 086 05 12.0 4
MINKLE CREEK
18 7.5 NOBLESVILLE
T/MORSE RES 051991
E 216TH ST BRDG .2 MI E OF HINKLE RO
11EPALES 2111204
0000 FEET DEPTH CLASS 00
DATE
FROM
TO
73/06/09
73/07/07
73/08/12
73/09/09
73/10/15
73/11/10
73/12/09
74/01/13
74/02/09
74/02/24
74/03/10
74/03/17
74/04/09
74/05/18
TIME DEPTH
OF
DAY FEET
13 20
11 30
09 25
13 30
12 00
14 15
13 15
08 00
09 50
10 30
09 30
09 30
08 20
00630
N02&N03
N-TOTAL
MG/L
7.400
3.100
2.080
0.610
1.740
1.500
3.400
3.360
3.300
4.200
3.500
3.400
3.600
5.100
00625
TOT KJEL
N
MG/L
0.600
1.100
2.400
0.560
0.500
0.250
0.300
0.400
0.500
0.900
0.600
0.500
0.800
0.700
00610
NH3-N
TOTAL
MG/L
0.080
0.160
0.066
0.042
0.012
0.008
0.024
0.048
0.025
0.105
0.025
0.015
0.025
0.060
00671
PHOS-DIS
ORTHO
MG/L P
0.046
0.120
0.132
0.044
0.032
0.012
0.020
0.016
0.020
0.090
0.020
0.020
0.050
0.015
00665
PHOS-TOT
MG/L P
0.095
0.160
0.065
0.050
0.020
0.045
0.025
0.030
0.145
0.035
0.045
0.125
0.070
-------
STORE! RETRIEVAL DATE 76/03/30
1829C1
40 09 40.0 086 02 00.0 4
LITTLE CICERO CREEK
18 7.5 ARCADIA
T/MORSE RES 051991
E 256TH ST dRDG .2 MI W OF SHERER AVE
1IEPALES 2111204
0000 FEET DEPTH CLASS 00
DATE
FROM
TO
73/06/09
73/07/07
73/08/12
73/09/09
73/10/15
73/11/10
73/12/09
74/01/13
74/02/09
74/02/24
74/03/10
74/03/17
74/04/09
74/05/18
00630 00625
TIME DEPTH N02&N03 TOT KJEL
OF N-TOTAL N
DAY FEET
13
12
09
13
12
14
13
08
10
11
10
10
08
40
00
40
45
30
30
35
30
45
10
00
00
40
MG/L
8
3
2
0
1
2
4
•
•
•
•
•
•
•
600
100
800
378
740
760
800
5.200
4
-------
STORE! RETRIEVAL DATE 76/03/30
183921 AS182931 POO 1450
40 07 44.0 086 01 15.0 4
CICERO
18 7.5 ARCADIA
D/MORSE RESERVOIR 051991
MORSE RESERVOIR
11EPALES 2141204 .
0000 FEET DEPTH CLASS 00
DATE
FROM
TO
73/06/19
CPU>-
73/06/19
73/07/24
CP(T>-
73/07/24
73/08/29
CP(T)-
73/08/29
73/10/03
CP(T)-
73/10/03
73/11/01
CP(T)-
73/11/01
74/02/01
CP(T)-
74/02/01
74/03/05
CP-
74/03/05
74/04/10
74/05/13
74/06/07
74/07/10
74/08/28
00630 00625
TIME DEPTH N02&N03 TOT KJEL
OF N-TOTAL N
DAY FEET MG/L MG/L
11
16
11
16
11
16
11
16
11
16
11
16
11
16
15
10
14
14
15
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
30
30
00
00
0
1
1
2
5
0
2
4
4
5
0
0
.360
.890
.820
.730
.100
.040
.240
.600
.900
.900
.120
.080
5.750
0.560
1.900
6.900
1.700
1.300
2.400
1.200
l.OOOK
2.050
4.600
6.000
00610 00671 00665 50051 50053
NH3-N PHOS-DIS PHOS-TOT FLOW CONDUIT
TOTAL ORTHO RATE FLOW-MOD
MG/L MG/L P MG/L P INST MGD MONTHLY
0.044
0.052
0.074
0.010K
0.010K
0.040K
0.086
0.050K
0.100
0.100
0.050K
0.050K
0.520
1.980
1.200
2.600
2.100
0.720
1.190
0.435
1.150
1.100
1.800
2.700
2.400
1.580
3.000
2.300
2.100
1.400
0.970
1.400
1.450
2.400
2.400
0
0
0
0
0
0
0
0
0
0
0
0
.156
.249
.151
.131
.156
.340
.338
.310
.174
.196
.136
.141
0.148
0.145
0.163
0.151
0.139
0.270
0.291
0.271
0.165
0.171
0.145
0.131
K VALUE KNOWN TO BE
LESS THAN INDICATED
-------
STORET RETRIEVAL DATE 76/03/30
DATE
FROM
TO
73/06/20
CP(T)-
73/06/20
73/07/22
73/08/22
73/09/24
73/10/22
73/11/28
73/12/24
74/01/29
74/02/26
74/03/27
74/04/27
74/05/28
74/06/30
00630
TIME DEPTH N02&N03
OF N-TOTAL
DAY FEET MG/L
08 00
20 00
08 00
08 00
15 00
08 00
08 00
08 00
08 00
08 00
08 00
08 30
08 00
08 00
7.800
11.200
8.500
6.700
13.600
5.700
7.700
5.880
6.600
3.600
4.800
6.100
8.500
1829CA AS1829CA P002000
40 07 45.0 086 11 45.0 4
SHERIDAN
18 HAMILTON CO MAP
T/MORSE RESERVOIR 051992
LITTLE CICERO CREEK
11EPALES 2141204
0000 FEET DEPTH CLASS 00
00625
TOT KJEL
N
MG/L
1.170
2.625
0.860
7.200
1.600
1.100
0.720
0.500
l.OOOK
2.000
1.800
1.300
4.550
00610
NH3-N
TOTAL
MG/L
0.005K
0.088
0.120
0.070
0.037
0.023
0.025
0.040K
0.050K
0.050K
0.100
0.050K
0.110
00671
PHOS-DIS
ORTHO
MG/L P
1.120
2.400
1.830
3.050
3.500
0.470
1.350
0.630
0.300
0.750
1.050
0.650
1.500
00665
PHOS-TOT
MG/L P
1.200
2.700
3.300
3.900
1.100
1.500
0.760
0.660
1.050
1.400
Oo650
1.730
50051
FLOW
RATE
INST MGD
0.380
0.300
0.295
0.300
0.230
0.557
0.400
0.460
0.450
0.396
0.292
0.456
0.390
50053
CONDUIT
FLOW-MGD
MONTHLY
0.250
0.250
0.300
0.250
0.250
0.270
0.340
0.400
0.250
0.406
0.400
0.400
0.400
K VALUE KNOWN TO BE
LESS THAN INDICATED
-------
STORE! RETRIEVAL DATE 76/03/30
00630
DATE TIME DEPTH N02&N03
FROM OF N-TOTAL
TO DAY FEET MG/L
74/06/20 09 00
CP-
74/06/20 15 00
2.500
5.300
1829AC TF1829AC P005500
40 17 17.0 086 01 50.0 4
TIPTON
18 TIPTON CO MAP
T/MORSE RESERVOIR 051792
CICERO CREEK
11EPALES 2141204
0000 FEET DEPTH CLASS 00
00625
TOT KJEL
N
MG/L
00610
NH3-N
TOTAL
MG/L
00671
PHOS-DIS
ORTHO
MG/L P
00665
PHOS-TOT
MG/L P
50051
FLOW
RATE
INST MOD
50053
CONDUIT
FLOW-MGD
MONTHLY
0.170
1.846
3.300
1.500
1.650
-------
STORET RETRIEVAL DATE 76/03/30
1S29AC TF1829AC POOSSOO
40 17 17.0 086 01 50.0 4
TIPTON
IS TIPTON CO HAP
T/MORSE RESERVOIR 051793
CICERO CREEK
11EPALES 2141204
0000 FEET DEPTH CLASS 00
DATE
FROM
TO
73/06/12
CP(T)-
73/06/12
73/07/12
CP(T>-
73/07/12
73/08/21
CP(T>-
73/08/21
73/09/05
CP-
73/09/05
73/10/19
CP(T>-
73/10/19
73/11/21
CP(T)-
73/11/21
73/12/12
CP(T)-
73/12/12
74/01/16
CP(T)-
74/01/16
74/02/13
CP-
74/02/13
74/03/14
CP(T)-
74/03/14
74/04/15
CP(T)-
74/04/15
74/05/15
CP(T)-
74/05/15
TIME DEPTH
OF
DAY
11
16
10
15
11
16
10
16
09
15
08
15
09
15
09
15
09
15
08
14
09
15
09
15
FEET
00
00
30
30
00
00
00
00
00
00
00
00
30
30
30
30
00
00
00
00
00
00
00
00
00630
N02&N03
N-TOTAL
MG/L
2.900
2.000
2.100
1.380
3.400
1.260
3.360
2.600
2.320
4.000
2.240
3.120
0062S
TOT KJEL
N
MG/L
6
5
5
8
6
4
5
5
6
9
1
1
.100
.300
.000
.400
.100
.400
.800
.400
.900
.000
.OOOK
.500
00610
NH3-N
TOTAL
MG/L
0.110
0.050
0.018
0.120
0.210
0.094
0.048
0.110
0.094
0.160
00671
PHOS-OIS
ORTHO
MG/L P
3.880
3.700
1.940
3.200
3.000
3.360
4.800
3.120
3.600
2.600
1.300
00665
PHOS-TOT
MG/L
4.
6.
4.
3.
6.
4.
4.
7.
3.
1.
P
700
400
000
750
000
000
750
600
450
750
50051
FLOW
RATE
INST MGD
1.700
1.300
1.400
1.300
1.000
1.200
1.500
1.500
1.700
1.600
1.400
2.000
50053
CONDUIT
FLOW-MGO
MONTHLY
1.430
1.600
1.280
1.520
1.300
1.100
1.230
1.400
1.600
1.800
1.600
1.650
K VALUE KNOWN TO BE
LESS THAN INDICATED
-------
STORET RETRIEVAL DATE 76/03/30
1829AB P01829AB P000700
40 13 00.0 086 01 12.0 4
ATLANTA
18 7.5 ARCADIA
T/MORSE RESERVOIR 051991
CICERO CREEK
11EPALES 2141204
0000 FEET DEPTH CLASS 00
DATE
FROM
TO
73/10/23
73/10/24
TIME DEPTH
OF
DAY FEET
10 00
10 00
00630
N02&N03
N-TOTAL
MG/L
0.040
0.036
00625
TOT KJEL
N
MG/L
4.400
2.900
00610
NH3-N
TOTAL
MG/L
0.154
0.007
00671
PHOS-DIS
ORTHO
MG/L P
1.350
1.150
00665
PHOS-TOT
MG/L P
1.850
1.400
50051
FLOW
RATE
INST MGD
0.022
0.022
50053
CONDUIT
FLOH-MGD
MONTHLY
0.021
0.021
-------
STORET RETRIEVAL DATE 76/03/30
1829AA TF1829AA P001338
40 10 30.0 086 00 47.0 4
ARCADIA
18 7.5 ARCADIA
T/MOHSE RESERVOIR 051991
CICERO CREEK
11EPALES 2141204
0000 FEET DEPTH CLASS 00
DATE
FROM
TO
73/06/29
73/07/30
73/08/30
73/10/29
73/11/30
73/12/28
74/02/27
74/04/15
74/05/22
74/06/20
74/07/23
74/08/14
00630
TIME DEPTH N02&N03
OF N-TOTAL
DAY FEET
09
10
16
10
16
09
15
16
13
10
13
14
30
00
00
00
00
00
00
00
30
30
30
20
MG/L
9.
a.
4.
5.
10.
6.
3.
3.
8.
5.
0.
10.
800
100
800
300
000
500
000
600
100
800
280
100
00625
TOT KJEL
N
MG/L
1.470
12.600
14.250
11.500
1.700
11.000
1.200
3.800
9.800
10.000
14.000
00610 00671 00665
NH3-N PHOS-DIS PHOS-TOT
TOTAL ORTHO
MG/L
0.270
0.880
2.510
0.400
0.120
0.059
0.610
0.220
0.170
0.420
0.820
0.740
MG/L P
1.050
4.800
4.640
2.940
1.000
0.510
1.850
1.750
0.750
1.840
2.500
4.400
50051 50053
FLOW CONDUIT
RATE FLOrt-MGD
MG/L P INST
1.650
5.200
5.600
5.200
1.600
0.540
2.700
2.600
1.250
2.900
3.200
5.300
0
0
0
0
0
0
0
0
0
0
0
0
MOD MONTHLY
.259
.106
.168
.160
.270
.290
.240
.230
.260
.210
.200
.200
0.198
0.149
0.205
0.200
0.200
0.230
0.240
0.250
0.240
0.240
0.220
0.240
------- |