U.S. ENVIRONMENTAL PROTECTION AGENCY
NATIONAL EUTROPHICATION SURVEY
WORKING PAPER SERIES
REPORT
ON
GEIST RESERVOIR
HAMILTON AND MARION COUNTIES
INDIANA
EPA REGION V
WORKING PAPER No, 327
CORVALLIS ENVIRONMENTAL RESEARCH LABORATORY - CORVALLIS, OREGON
and
ENVIRONMENTAL MONITORING & SUPPORT LABORATORY - LAS VEGAS, NEVADA
699-440
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REPORT
ON
GEIST RESERVOIR
HAMILTON AND WRION COOTIES
INDIANA
^ EPA REGION V
en
WORKING PAPER No, 327
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 Sunmary 5
IV. Nutrient Loadings 9
V. Literature Reviewed 16
VI. Appendices 17
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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)K 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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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, II. 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
Pigeon
Syl van
Ti ppecanoe
Versailles
Wawassee
Webster
Westler
Whitewater
Winona
Wi trier
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
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- 40-00'
Map Location
(indT
*\
Fall
Creek
GEIST RESERVOIR
(g) Tributary Sampling Site
X Lake Sampling Site
P Sewage Treatment Facility
^•Drainage Area Boundary
9 _J IP Km.
s Mi.
Scale
39°50'
85' 50
85° 40'
85'30
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GEIST RESERVOIR
STORE! NO. 1811
I. CONCLUSIONS
A. Trophic Condition:
Survey data indicate that Geist Reservoir is eutrophic. It
ranked 17th when the 27 Indiana lakes sampled in 1973 were compared
using a combination of six parameters*. Nineteen of the lakes
had less median total phosphorus, nine had less median dissolved
phosphorus, 17 had less median inorganic nitrogen, 23 had less
mean chlorophyll a_, and 22 had greater mean Secchi disc trans-
parency.
Survey limnologists noted emergent and submerged aquatic macro-
phytes at sampling station 2 and emergent macrophytes along parts
of the shoreline.
B. Rate-Limiting Nutrient:
The algal assay results indicate that Geist Reservoir was
limited by phosphorus at the time the sample was taken (05/10/73).
The reservoir data indicate phosphorus limitation at all sampling
times.
C. Nutrient Controllability:
1. Point sources—During the Survey sampling year, five point
sources provided samples. In May of 1975, the Indiana Division of
Water Pollution Control identified six additional point sources in
* See Appendix A.
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2
the Fall River drainage, determined the phosphorus contribution
of four of them, and provided the data for this report (Bon-
Honrne, 1976). The inclusion of the additional point-source loads
permits a more realistic assessment of phosphorus controllability.
It is calculated that the phosphorus contribution of point
sources accounted for 32.5% of the total load to Geist Reservoir.
The Fortville wastewater treatment plant contributed 10.9%, the
Indiana State Reformatory plant contributed 7.6%, and the Middletown
plant contributed 6.1% of the total. The remaining six measured
point sources collectively contributed 8.0% of the total phosphorus
load. The loads from an elementary school and a church camp were
not determined but probably were relatively insignificant compared
to the measured sources.
The reservoir loading of 2.87 g/m2/yr is three times that pro-
posed by Vollenweider (Vollenweider and Dillon, 1974) as a eutro-
phic loading (see page 15). However, the mean hydraulic retention
time of the reservoir is a relatively short 58 days, and Vollen-
weider 's model may not apply.
While even complete removal of phosphorus at the listed point
sources would still leave a loading of 1.9 g/m2/yr (ca. twice the
eutrophic loading), in view of the questionable applicability of
Vollenweider's model and the phosphorus-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
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3
the trophic condition of the reservoir.
2. Non-point sources—The phosphorus contributions of non-
point sources accounted for 67.2% of the total input to the
reservoir. Fall Creek contributed 48.6%, and the remaining
three sampled tributaries collectively contributed 12.5% of the
total load. The ungaged tributaries were estimated to have con-
tributed 5.5% of the total.
The phosphorus export rate of Dry Branch was a rather high
57 kg/km2/yr. The higher rate may be due in part to the un-
measured McCordsville Elementary School septic-tank load and in
part to septic tank drainage from the community of McCordsville.
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4
II. LAKE AND DRAINAGE BASIN CHARACTERISTICS1"
A. Lake Morphometry :
1. Surface area: 7.28 kilometers2.
2. Mean depth: 3.6 meters.
3. Maximum depth: 6.7 meters.
4. Volume: 26.208 x 106 m3.
5. Mean hydraulic retention time: 58 days.
B. Tributary and Outlet:
(See Appendix C for flow data)
1. Tributaries -
Drainage Mean flow
Name area (km2)* (m3/_sec)*
Fall Creek 440.8 4.21
Dry Branch 19.7 0.18
Flatfork Creek 26.9 0.25
Thorpe Creek 24.6 0.23
Minor tributaries &
immediate drainage - 39 .j 0.35
Totals 551.9 5.22
2. Outlet -
Fall Creek 559.2** 5.22**
C. Precipitation***:
1. Year of sampling: 122.0 centimeters.
2. Mean annual: 100.8 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 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
Geist 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 two 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
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 4.3 meters at station 1 and 6.1 meters
at station 2.
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 1MG/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)
CHLHPYL A (UG/L)
SECCHI (METERS)
A. SUMMARY OF PHYSICAL AND
1ST SAMPLING ( 5/10/73)
2 SITES
CHEMICAL CHARACTERISTICS FOR
STORET CODE 1811
GEIST RESERVOIR
2ND SAMPLING ( 8/ 2/73)
2 SITES
3RD SAMPLING 110/15/73)
2 SITES
RANGE
16.2
7.8
530.
8.1
196.
0.050
0.004
2.210
0.060
0.600
2.280
2.920
34.9
O.S
- 18.2
- 11.2
- 590.
8.4
- 260.
- 0.089
- 0.013
- 3.020
- 0.150
- 0.800
- 3.140
- 3.690
- 54.2
0.9
MEAN
17.3
9.5
560.
8.3
223.
0.063
0.007
2.641
0.079
0.700
3.720
3.341
44.5
0.7
MEDIAN
17.3
9.6
560.
8.3
198.
0.058
0.006
2.890
0.060
0.700
2.950
3.590
44.5
0.7
RANGE
25.3
3.4
442.
7.7
159.
0.043
0.009
0.330
0.030
1.100
0.360
2.090
17.4
0.4
- 26.3
- 10.8
- 491.
8.6
- 185.
- 0.179
- 0.027
- 0.990
- 0.330
- 2.200
- 1.320
- 2.530
- 94.1
1.0
MEAN
25.9
7.7
46f.
8.4
170.
0.097
0.014
0.740
0.128
1.520
0.868
2.260
55.7
0.7
MEDIAN
26.0
8.8
453.
8.5
163.
0.059
0.010
0.990
0.090
1.200
1.080
2.190
55.7
0.7
RANGE
19.6
6.8 .
391.
8.3
151.
0.074
0.006
0.060
0.070
0.900
0.150
0.970
4.7
0.6
- 20.8
7.8
- 458.
8.4
- 190.
- 0.137
- 0.016
- 0.120
- 0.120
- 1.200
- 0.210
- 1.320
- 70.4
0.8
MEAN
20.3
7.2
418.
8.3
166.
0.098
0.011
0.079
0.104
1.057
0.183
1.136
37.5
0.7
MEDIAN
20.6
7.0
394.
8.3
155.
0.092
0.009
0.080
0.110
1.000
0.180
1.080
37.5
0.7
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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.
Cyclotella sp.
Dactylococcopsis sp,
Asterionella sp.
Stepjianodiscus sp.
Other genera
Total
Centric diatoms
Flagellates
Melosira S£.
Eucjlena sp.
Synedra sp.
Other genera
Total
Centric diatoms
Melosira sp.
Flagellates
Oscillatoria sp.
Merismopedia sp.
Other genera
Total
Station
Number
1
2
1
2
1
2
Algal Units
per ml
1,803
1,277
992
947
841
5,438
11,298
11,605
9,579
6,868
468
426
2.884
31,830
14,908
4,820
3,479
2,335
1,888
8.251
35,681
Chlorophyll
(yg/D
54.2
34.9
94.1
17.4
70.4
4.7
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8
C. Limiting Nutrient Study:
1. Autoclaved, filtered, and nutrient spiked -
Ortho P Inorganic N Maximum yield
Spike (mq/1) Cone, (mg/1) Cone, (mg/1) (mg/1-dry wt.)
Control 0.015 2.380 3.4
0.050 P 0.065 2.380 20.6
0.050P+1.0N 0.065 3.380 21.8
1.0 N 0.015 3.380 2.9
2. Discussion -
The control yield of the assay alga, Selenastrum capri-
cornutum, indicates that the potential primary productivity
. of Geist Reservoir was moderately high at the time the sample
was taken (05/10/73). Also, a six-fold increase in yield
with the addition of only phosphorus indicates the reservoir
was phosphorus limited at that time. Note that the addition
of only nitrogen resulted in a yield not significantly dif-
ferent from that of the control.
The reservoir data also indicate phosphorus limitation;
i.e., the mean inorganic nitrogen to orthophosphorus ratios
were 17 to 1 or greater at all sampling times, 'and phosphorus
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 reservoir.
Except for Flatfork Creek, nutrient loads for sampled tributaries
were determined by using a modification of a U.S. Geological Survey
computer program for calculating stream loadings*. The phosphorus
load measured in Flatfork Creek at station C-l was less than the
Fortville wastewater treatment plant load, and the non-point nutrient
loads of this stream were estimated (see below). The Fall Creek
nutrient loads shown are those measured minus the point-source loads.
Nutrient loads for Flatfork Creek and unsampled "minor tributaries
and immediate drainage" ("ZZ" of U.S.G.S.) were estimated using the
nutrient loads at station D-l, in kg/km2/year, and multiplying by the
Flatfork Creek and ZZ areas in km2.
* See Working Paper No. 175.
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10
The operators of the Indiana State Reformatory, Pendleton, Middle-
town, Fortville, and Shenandoah High School wastewater treatment plants
provided monthly effluent samples and corresponding flow data.
The estimated phosphorus load from septic tanks was reduced by
50% to adjust for a phosphate detergent ban which has been in effect
in Indiana since January, 1972.
A. Waste Sources:
1. Known domestic -
Name
Indiana State
Reformatory
Pendleton
Middletown
Fortville
Ingalls
Regency MHP
Shenandoah
High Sch.*
McCordsville
El em. Sch.
U. Pentecostal
Camp
Pop.
Served
2,300
2,496
2,300
2,480
888
?
700
?
?
Treatment
tr. filter
act. sludge
tr. filter
tr. filter
septic tanks
ext. aer.
+ pond
act. sludge
septic tank
ext. aer.
Mean Flow
(mVd)
1,403.3
881.4
1,539.5
1,860.8
336.1
11.4
11.4
?
113.6**
Receiving
Water
Fall Creek
Fall Creek
Fall Creek
Flatfork Creek
Lick Creek
Fall Creek
Deer Creek
Stansbury Ditch/
Dry Branch
Lick Creek
t Treatment plant questionnaires; Anonymous, 1971.
* School operates 9 mo./year; pop. equivalent=125.
** Design flow.
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11
2. Known industrial* -
Name
E. I. DuPont
Nemours Co.
Brookside Corp.
#1
#2
Forthrite Div.,
Richardson Co.
#1
#2
Treatment
neutralization
metal recovery
lagoon
(washwater)
septic tank
Mean Flow
(m'/d)
26.5
75.7
128.7
50.7
no discharge
Receiving
Water
Stottlemeyer
Ditch/Flat-
fork Creek
Dry Branch Creek
Dry Branch Creek
Stansbury Ditch/
Dry Branch
Stansbury Ditch/
Dry Branch
BonHomme, 1976.
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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) -
Fall Creek 10,175 48.6
Dry Branch 1,130 5.4
Flatfork Creek 780 3.7
Thorpe Creek 710 3.4
b. Minor tributaries & immediate
drainage (non-point load) - 1,155 5.5
c. Known domestic STP's -
Indiana State Reformatory 1,600 7.6
Pendleton 930 4.4
Middletown 1,270 6.1
Fortville 2,275 10.9
Regency MHP 110 0.5
Shenandoah High School 10 <0.1
McCordsville El em. Sch. ?
Pentecostal Camp ?
d. Septic tanks* - 55 0.3
e. Known industrial -
E. I. DuPont Nemours 60 0.3
Brookside Corp. 540 2.6
Forthrite Div. 20 <0.1
f. Direct precipitation** - 125 0.6
Total 20,945 100.0
2. Outputs -
Lake outlet - Fall Creek 12,625
3. Net annual P accumulation - 8,320 kg.
* Estimate based on 1970 Census of Ingalls and 38 lakeshore dwellings; see
Working Paper No. 175.
** See Working Paper No. 175.
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13
C. Annual Total Nitrogen Loading - Average Year:
1. Inputs -
kg N/ % of
Source yr total
a. Tributaries (non-point load) -
Fall Creek 444,795 66.8
Dry Branch 36,200 5.4
Flatfork Creek 45,435 6.8
Thorpe Creek 41,545 6.2
b. Minor tributaries & immediate
drainage (non-point load) - 67,390 10.1
c. Known domestic STP's -
Indiana State Reformatory 2,850 0.4
Pendleton 3,750 0.6
Middletown 5,155 0.8
Fortville 6,390 1.0
Regency MHP ?
Shenandoah High School 20 <0.1
McCordsville El em. Sch. ?
Pentecostal Camp ?
d. Septic tanks* - 4,190 0.6
e. Known industrial -
E. I. DuPont Nemours ?
Brookside Corp. ?
Forthrite Div. ?
f. Direct precipitation** - 7.860 1.2
Total 665,580 100.0
2. Outputs -
Lake outlet - Fall Creek 681,175
3. Net annual N loss - 15,595 kg.
* Estimate based on 1970 Census of Ingalls and 38 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/km2/yr kg N/km2/yr
, Fall Creek 23 1,009
Dry Branch 57 1,838
Thorpe Creek 29 1,689
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15
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 2.88 1.14 91.4 loss*
Vollenweider phosphorus loadings
(g/m2/yr) based on mean depth and mean
hydraulic retention time of Geist Reservoir:
"Dangerous" (eutrophic loading) 0,92
"Permissible" (oligotrophic loading) 0.46
* There was an apparent nitrogen loss during the sampling year. This may
have been due to nitrogen fixation in the reservoir, solubilization of
previously sedimented nitrogen, recharge with nitrogen-rich ground water,
or unknown point sources discharging directly to the reservoir. What-
ever the cause, a similar loss has occurred at Shagawa Lake, Minnesota,
which has been intensively studied by EPA's former National Eutrophication
and Lake Restoration Branch (Malueg et al., 1975).
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16
V. LITERATURE REVIEWED
Anonvmous, 1971. Inventory of waste treatment facilities. EPA Publ.
OWP-1, vol. 5, Wash., DC.
BonHomme, Harold L., 1976. Personal communication (review of pre-
liminary report; point-source data). IN Div. of Water Poll. Contr.,
Indianapolis.
Malueg, Kenneth W., D. Phillips Larsen, Donald W. Schults, and Howard
T. Mercier; 1975. A six-year water, phosphorus, and nitrogen bud-
get for Shagawa Lake, Minnesota. Jour. Environ. Qual., vol. 4,
no. 2, pp. 236-242.
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 (reservoir morphometry).
IN Div. of 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
1837
1828
1829
1836
1837
1839
1840
1841
1842
1843
1844
18*5
1846
1847
1848
1849
1850
1851
.852
1853
1854
1855
1856
1857
LAKE NAME
CATARACT LAKE
GEIST RESERVOIR
JAMES LAKE
MISS1SSINEKA RESERVOIR
MONKOE RESERVOIR
MORSE RESERVOIR
HAHASEE LAKE
WEBSTER LAKE
WHITEWATER LAKE
WINONA LAKE
WESTLER LAKE
WITMER 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
1.66Q
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
.623
.222
.500
.000
.167
.667
.125
.333
.400
.500
.333
.333
.000
.833
.333
.000
.375
.111
.444
.667
.667
.333
.167
MEAN
CHLOHA
10
45
11
15
b
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 OrtTriO f
0.01J
0.009
0.008
0.029
o.oor
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 (NUMBKK OF LAKES WITH HIGHEx VALUES*
LAKE
CODE
1805
1811
1817
1827
1828
1H29
1836
1837
Ift39
1840
1841
1842
1843
1844
1845
1846
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
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 f
37
27
73
12
67
?3
94
67
19
50
50
50
77
85
62
94
100
4
31
8
42
81
88
0
37
15
58
I 9)
( 7)
( 191
( 31
( 17)
( 6)
( 24)
( 17)
( 5)
( 12)
( 12)
I 12)
I 20)
( 22)
( 16)
I 24)
( 26)
( D
( 6)
( 2)
( 11)
( 21)
I 23)
( 0)
( 9)
( 4)
( 15)
MEDIAN
INOWG N
15
35
42
4
b9
0
85
62
19
27
54
50
81
88
58
23
46
96
38
31
77
100
92
12
8
73
65
( 41
( 9)
( 11)
( 1)
I 18)
( 0)
< 22)
( 16)
( 5)
( 7)
( 14)
( 13)
( 21)
< 23)
( 15)
( 6)
< 12)
( 25)
( 10)
( 8)
( 201
( 26)
( 24)
( 3)
( 2)
( 19)
( 17)
500-
MEAN SEC
31
15
be
8
54
12
96
62
23
38
65
50
85
92
69
81
88
27
0
4
19
77
100
44
44
35
73
( 8)
( 4)
( 15)
( 2)
( 14)
( 3)
o
< 25)
( 16)
( 6)
( 10)
( 17)
( 13)
( 22)
( 24)
( 18)
( 21)
( 23)
( 7)
( 0)
( 1)
( 5)
I 20)
( 26)
( 11)
( 11)
( 9)
( 19)
MEAN
CHLORA
62
12
50
38
73
4
88
54
19
58
65
42
85
77
69
92
100
8
0
27
23
81
96
35
46
15
31
( 16)
I 3)
I 13)
( 10)
( 19)
( 1>
I 23)
( 14)
( 5)
( 15)
( 17)
( 11)
( 22)
( 20)
( 18)
( 24)
( 26)
( 2)
( 0)
( 7)
( 6)
I 21)
( 25)
I 9)
I 12)
I 4)
I H)
15-
MIN DO
35
92
35
35
35
35
85
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)
I 0)
< 221
( 0)
( 0)
( 0)
( 0)
( 0)
( 0)
( 0)
( 0)
I 19)
( 20)
( 20)
( 25)
( 23)
( 26)
I 0)
I 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
23
12
15
46
75
75
0
27
4
19
( 9)
I 16)
1 17)
( 2)
( 18)
( 15)
< 251
( 21)
I ID
( 13)
( 9)
( 13)
( 25)
( 22)
( B>
( 24)
< 23)
( 6)
I 31
( 4)
( 12)
( 19)
( 19)
( 0)
( 7)
( 1)
( 5)
INJEX
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
141
177
231
-------
LAKES RANKED sr INDEX NOS.
RANK LAKE CODE LAKE NAME INDEX NO
1 1836 WAMASEE LAKE 546
2 1847 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 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 HOVEY LAKE 177
23 1850 VERSAILLES LAKE 173
24 1839 ilHITEHATER LAKE 157
25 1629 MORSE RESERVOIR 132
26 1854 LONG LAKE 126
27 1827 MISSISSINEKA RESERVOIR 105
-------
APPENDIX B
CONVERSION FACTORS
-------
CONVERSION FACTORS
Hectares x 2.471 = acres
Kilometers x 0.6214 = miles
Meters x 3.281 = feet
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 Iftll GEIST RESERVOIR
TOTAL DRAINAGE AREA OF LAKE(SO KM)
SUB-DRAINAGE
TRIBUTARY AREA(SQ KM)
JAN
FEB
557.1
MAR
APR
MAY
NORMALIZED FLOWS(CMS)
JUN JUL AUG
SEP
OCT
NOV
DEC
MEAN
leiiAi
1811A2
1811B1
1811C1
181101
1811ZZ
559.2
440.8
19.7
26.9
24.6
37.8
7.39
5.78
0.227
0.311
0.283
0.453
8.16
6.43
0.280
0.396
0.340
0.538
11.10
8.78
0.425
0.566
0.510
0.765
10.62
8.38
0.368
0.510
0.481
0.708
7.02
5.52
0.241
0.340
0.311
0.453
5.18
4.08
0.184
0.252
0.232
0.368
3.26
2.55
0.110
0.150
0.139
0.212
1.47
1.13
0.034
0.048
0.045
0.071
1.25
0.96
0.034
0.048
0.042
0.068
1.39
1.08
0.037
0.051
0.045
0.074
2.75
2.18
0.096
0.130
0.119
0.184
4.81
3.79
0.181
0.246
0.227
0.340
5.35
4.21
0.184
0.253
0.230
0.351
SUMMARY
TOTAL DRAINAGE AREA OF LAKE =
SUM OF SUB-DRAINAGE AREAS =
557.1
549.9
TOTAL FLOW IN =
TOTAL FLOW OUT =
62.93
64.39
MEAN MONTHLY FLOWS AND DAILY FLOWS(CMS)
TRIBUTARY MONTH YEAR MEAN FLOW DAY
1811A1
FLOW DAY
FLOW DAY
FLOW
1811A2
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
9.628
3.115
2.973
1.699
1.841
4.248
11.327
19.255
9.911
11.327
12.176
7.646
6.881
2.461
2.353
1.201
1.280
2.973
7.929
13.451
7.051
8.042
8.552
5.409
9
8
12
9
16
10
9
12
9
10
7
12
9
8
12
9
16
10
9
12
9
10
7
12
11.044
3.115
7.362
1.614
1.869
1.841
3.681
4.814
9.345 24
8.495 17
13.026
10.477
7.872
2.209
5.125
1.133
1.303
1.274
2.605
3.398
6.598 24
5.947 17
9.146
7.391
11.327
10.336
8.099
7.362
-------
TRIBUTARY FLOW INFORMATION FOR INDIANA
03/29/76
LAKE CODE 1811
GEIST RESERVOIR
MEAN MONTHLY FLOWS AND DAILY FLOWS
TRIBUTARY MONTH YEAR MEAN FLOW DAY
181161
1811C1
181101
1811ZZ
6
7
8
9
10
11
12
I
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
0.309
0.051
0.045
0.011
0.011
0.074
0.340
0.595
0.311
0.368
0.368
0.241
0.425
0.147
0.144
0.074
0.079
0.178
0.481
0.821
0.425
0.481
0.538
0.340
0.368
0.076
0.071
0.020
0.023
0.108
0.425
0.736
0.396
0.453
0.481
0.311
0.595
0.212
0.201
0.102
0.110
0.255
0.680
1.161
0.595
0.680
0.736
0.453
9
8
12
9
16
10
9
12
9
10
7
12
9
10
12
9
16
10
9
12
9
10
7
12
9
8
12
9
13
10
9
12
9
10
7
12
9
a
12
9
13
10
9
12
9
10
7
12
FLOW DAY
FLOW DAY
FLOW
0.340
0.040
0.224
0.008
0.011
0.011
0.054
0.099
0.283
0.266
0.396
0.340
0.481
0.119
0.311
0.068
0.082
0.074
0.159
0.207
0.396
0.368
0.566
0.453
0.425
0.062
0.278
0.017
0.023
0.023
0.085
0.136
0.368
0.311
0.510
0.396
0.680
0.190
0.453
0.096
0.110
0,110
0.224
0.283
0.566
0.510
0.793
0.623
24
17
24
17
24
17
10
16
24
17
0.368
0.340
0.481
0.453
0.453
0.396
0.164
0.113
0.708
0.623
-------
APPENDIX D
PHYSICAL and CHEMICAL DATA
-------
STORET RETRIEVAL DATE 76/03/30
181101
39 55 59.0 085 56 17.0 3
GEIST RESERVOIR
18057 INDIANA
051992
DATE
FROM
TO
73/05/10
73/03/02
73/10/15
DATE
FROM
TO
73/05/10
73/08/02
73/10/15
TIME
OF
DAY
11 10
11 10
11 10
15 05
15 05
10 20
10 20
10 20
TIME
OF
DAY
11 10
11 10
11 10
15 05
15 05
10 20
10 20
10 20
DEPTH
FEET
0000
0006
0014
0000
0005
0000
0005
0008
DEPTH
FEET
0000
0006
0014
0000
0005
0000
0005
0008
00010
WATER
TEMP
CENT
18.2
18.1
17.5
26.2
25.8
19.9
19.6
19.6
00665
PHOS-TOT
MG/L P
0.089
0.050
0.067
0.179
0.157
0.095
0. 137
0.133
00300 00077 00094
DO TRANSP CNDUCTVY
SECCHI FIELD
MG/L INCHES MICROMHO
11.2
9.1
10.8
7.8
7.6
32217
CHLRPHYL
A
UG/L
54.2
94.1
70.4
21 590
580
580
14 491
489
24 444
458
456
HEPALES 2111202
0018 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
8.20
8.30
8.10
8.60
8.50
8.40
8.40
8.30
MG/L
260
260
250
185
182
178
190
184
MG/L
0.060
0.060
0.080
0.030
0.080
0.120
0.090
0.070
MG/L
0.700
0.700
0.800
2.200
2.000
1.200
1.200
1.000
MG/L
2.220
2.240
2.210
0.330
0.400
0.080
0.120
0.080
MG/L P
0.013
0.008
0.009
0.027
0.015
0.015
0.016
0.015
-------
STORET RETRIEVAL DATE 76/03/30
181102
39 54 38.0 085 58 56.0 3
GEIST RESERVOIR
18097 INDIANA
051992
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
11 45 0000
11 45 0004
11 45 0015
11 45 0020
14 55 0000
14 55 0005
14 55 0017
10 40 0000
10 40 0005
10 40 0010
10 40 0018
TIME DEPTH
OF
DAY FEET
11 45 0000
11 45 0004
11 45 0015
11 45 0020
14 55 0000
14 55 0005
14 55 0017
10 40 0000
10 40 0005
10 40 0010
10 40 0018
00010
WATER
TEMP
CENT
17.3
17.0
16.8
16.2
26.3
26.0
25.3
20.8
20.7
20.7
20.6
00665
PHOS-TOT
MG/L P
0.070
0.057
0.051
0.058
0.059
0.049
0.043
0.074
0.077
0.081
0.092
00300
DO
MG/L
9.9
9.6
7.8
8.8
3.4
6.8
6.8
7.0
32217
CHLRPHYL
A
UG/L
34.9
17.4
4.7
00077 00094
TRANSP CNDUCTVY
SECCHI FIELD
INCHES MICROMHO
34 530
540
540
560
40 444
442
453
32 391
393
394
392
11EPALES 2111202
0023 FEET DEPTH CLASS 00
00400 00410 00610 00625
PH T ALK NH3-N TOT KJEL
SU
8
8
8
8
8
8
7
8
8
8
8
.40
.40
.30
.30
.50
.50
.70
.40
.30
.30
.30
CAC03
MG/L
198
198
196
197
159
160
163
151
155
152
152
TOTAL
MG/L
0.060
0.060
0.080
0.150
0.110
0.090
0.330
0.120
0.110
0.100
0.120
N
MG/L
0.700
0.600
0.700
0.700
.200
.100
.100
.000
.900
.000
.100
00630
N02&N03
N-TOTAL
MG/L
2.890
3.020
2.920
2.990
0.990
0.990
0.990
0.080
0.070
0.060
0.060
00671
PHOS-DIS
ORTHO
MG/L P
0.006
0.005
0.004
0.005
0.009
0*009
0.010
0.009
0.009
0.006
0.006
-------
APPENDIX E
TRIBUTARY and WASTEWATER
TREATMENT PLANT DATA
-------
STORE! RETRIEVAL DATE 76/03/30
39 53 55.0 085 59 29.0 4
FALL CREEK
18 7.5 MCCORDSVILLE
0/GFIST RES 051992
79TH ST 6RDG BELO GEIST RES 0AM
11EPALES £111204
0000 KEET DEPTH CLASS 00
DATE
FROM
TO
73/06/09
73/07/08
73/08/12
73/09/09
73/10/16
73/11/10
73/12/09
74/01/12
74/02/09
74/02/24
74/03/10
74/03/17
74/04/07
74/05/12
00630 00625
TIME DEPTH N020N03 TOT KJEL
OF N- TOTAL N
DAY FEET
10
11
10
14
18
11
10
10
14
13
10
10
15
14
40
00
?0
?5
45
30
45
20
40
00
00
30
10
10
MG/L
9.
2.
1.
0.
1.
1.
3.
3.
3.
4.
3.
2.
4.
3.
500
040
380
530
060
040
500
080
600
200
780
900
300
250
MG/L
1.
0.
3.
0.
0.
0.
1.
0.
0.
1.
0.
0.
0.
1.
500
350
400
320
400
250
000
400
200
700
400
600
900
100
00610 00671 00665
NH3-N PHOS-DIS PHOS-TOT
TOTAL UKTHO
MG/L
0.
0.
0.
u.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
050
024
060
015
023
009
032
056
030
090
030
025
020
125
MG/L
0.
3.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
p
054
031
032
057
017
02ft
044
020
100
020
020
035
050
MG/L P
0.115
0.045
0.055
0.085
0.040
0.028
0.055
0.030
0.150
0.055
0.070
0.070
0.170
-------
STORE! RETRIEVAL UATE 76/03/30
ldllA2
39 57 16.0 085 52 01.0 4
FALL CHEEK
18 7.5 INGALLS
I/GE1ST KES 051992
ST HkY 238 BRDG 2 MI NNW OF FOKTVILLE
11EPALES 2111204
0000 FEET DEPTH CLASS 00
00630
DATE
FROM
TO
73/06/09
73/07/08
73/08/12
73/09/09
73/10/16
73/11/10
73/12/09
74/01/12
74/02/09
74/02/24
74/03/10
74/03/17
74/04/07
74/05/12
TIME DEPTH
OF
DAY
12
11
09
13
18
10
09
12
13
14
10
09
14
13
NI02&N03
N-TOTAL
FEET
35
30
10
45
05
38
45
25
45
10
00
30
?0
?0
MG/L
5
2
1
1
1
1
2
3
3
2
3
3
3
2
.400
.400
.340
.700
.460
.560
.520
.500
.400
.100
.300
.000
.600
.400
00625
TOT KJEL
N
MG/L
1.100
0.380
1.890
0.840
0.550
0.200
0.400
0.300
0.700
0.500
0.600
0.600
0.800
1.000
00610
NH3-N
TOTAL
MG/L
0
0
0
0
0
0
0
0
0
0
0
0
0
0
.069
.016
.061
.078
.039
.023
.048
.012
.055
.055
.025
.030
.030
.047
00671
PHOS-DIS
00665
PHOS-TOT
ORTHO
MG/L
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
P
052
075
110
096
115
084
048
020
030
155
0.035
0.
0.
0.
035
035
022
MG/L P
0
0
0
0
0
0
0
0
0
0
0
0
0
.140
.115
.150
.170
.102
.065
.030
.055
.175
.105
.090
.065
.120
-------
STORE! RETRIEVAL DATE 76/03/30
1811B1
39 54 05.0 085 57 50.0 4
DRY BRANCH
18 7.5 MCCORDSVILLE
T/GEIST RES 051992
FOX RL) BKDG 1.5 MI N OF OCKLANDON
11EPALES 2111204
0000 FEET DEPTH CLASS 00
DATE
FROM
TO
73/06/09
73/07/08
73/08/12
73/09/09
73/10/16
73/11/10
73/12/09
74/01/12
74/02/09
74/02/24
7W03/10
74/03/17
74/04/07
74/05/12
00630 00625
TIME DEPTH N02&N03 TOT KJEL
OF N-TOTAL N
DAY FEET
11
10
10
14
18
11
10
11
14
13
10
09
14
13
45
?0
07
10
30
10
35
15
30
30
30
10
50
45
MG/L
10
4
1
0
0
1
4
5
5
4
<+
4
5
7
.600
.600
.000
.051
.790
.510
.600
.600
.000
.100
.900
.700
.460
.500
MG/L
6.
0.
1.
1.
0.
0.
0.
0.
0.
0.
0.
0.
0.
2.
400
790
540
760
750
650
500
400
700
800
500
600
400
500
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.
480
042
150
165
020
039
096
008
030
090
025
025
005K
560
MG/L P
0.079
0.680
0.236
0.510
0.580
0.080
0.020
0.050
0.090
0.085
0.085
0.025
0.230
MG/L P
0
0
0
0
0
0
0
0
0
0
0
0
0
.125
.880
.500
.620
.605
.105
.030
.075
.165
.130
.128
.030
.350
K VALUE KNOWN TO BE
LESS THAN INDICATED
-------
STORE! RETRIEVAL DATE 76/03/30
1811C1
39 56 30.0 085 52 30.0 4
FLATFORK CHEEK
18 7.5 MCCOROSVILLE
T/GEIST RES- 051992
CONNECTICUT AVE BRDG 1.5 MI W OF FOKTVIL
11EPALES 2111204
0000 FEET DEPTH CLASS 00
DATE
FROM
TO
73/07/10
73/08/12
73/09/09
73/10/16
73/11/10
73/12/09
74/01/12
74/02/09
74/02/24
74/03/10
74/03/17
74/04/07
74/05/12
00630 00625
TIME DEPTH N02&N03 TOT KJEL
OF N-TOTAL N
DAY FEET
16
09
13
18
10
09
12
13
13
11
12
14
13
00
15
50
10
45
55
00
50
30
00
00
25
25
MG/L
1
1
1
1
1
2
4
3
4
3
2
3
3
.980
.320
.500
.200
.440
.400
.100
.200
.100
.000
.900
.200
.600
MG/L
0.
1.
0.
0.
0.
0.
0.
0.
1.
0.
0.
0.
0.
480
260
460
400
150
500
500
300
000
400
500
500
900
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.
031
052
044
006
009
026
068
005
110
010
010
010
060
MG/L
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
P
023
073
046
039
016
024
068
015
090
020
050
017
025
MG/L P
0.055
0.070
0.075
0.020
0.030
0.095
0.025
0.140
0.050
0.055
0.040
0.105
-------
STORE! RETRIEVAL DATE 76/03/30
1H1101
39 57 17.0 085 54 31.0 4
THORPE CREEK
18 7.5 MCCOWOSVILLE
T/GEIST RES 051992
E 113TH ST BRDG 3.5 MI WNM OF FORTVILLE
HEPALES 2111204
0000 FEET DEPTH CLASS 00
DATt
FROM
TO
73/06/09
73/07/08
73/08/12
73/09/09
73/10/13
73/11/10
73/12/09
74/01/12
74/02/09
74/02/24
74/03/10
7W03/17
74/04/07
74/05/12
00630 00625
TIME DEPTH N02&N03 TOT KJEL
OF N-TOTAL N
DAY FEET
12
11
09
13
07
10
09
10
13
13
10
11
14
13
05
00
05
40
50
30
30
25
30
40
45
30
10
15
MG/L
9.
4.
2.
0.
0.
1.
5.
2.
5.
4.
6.
6.
6.
5.
900
300
200
770
610
430
040
900
700
100
300
100
800
200
MG/L
1.
0.
2.
1.
0.
0.
0.
0.
0.
1.
0.
0.
0.
1.
320
540
310
000
780
300
300
300
200
000
400
400
600
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.
082
066
110
058
044
007
008
016
012
130
010
010
005
030
MG/L
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
p
065
042
220
037
063
014
020
020
015
090
020
020
020
010
MG/L P
0.105
0.065
0.560
0.125
0.105
0.025
0.025
0.020
0.020
0.140
0.035
0.030
0.035
0.060
-------
STORE! RETRIEVAL DATE 76/03/30
IflllXA P01611XA P000125
40 00 30.0 085 30 30.0 4
SHENANOOAH HI SCHOOL
18 HENRY CO HWY MAP
T/GEIST RESERVOIR 051991
SUGAR CREEK
11EPALES 2141204
0000 FEET DEPTH CLASS 00
DATE
FROM
TO
73/06/29
73/07/30
73/08/29
73/09/24
73/10/31
73/11/28
73/12/17
74/01/16
74/02/20
74/03/25
74/04/23
74/05/22
74/06/14
00630 00625 00610 00671 00665 50051 50053
TIME DEPTH N02&N03 TOT KJEL NH3-N PHOS-DIS PHOS-TOT FLOW CONDUIT
OF N-TOTAL N TOTAL ORTHO RATE FLOW-MGD
DAY FEET MG/L MG/L MG/L MG/L P MG/L P INST MGD MONTHLY
08 35 0.210 2.300 0.084 5.430 5.800
08 35 0.160 1.900 0.042 3.700 4.100
12
11
09
13
11
13
10
15
07
12
14
30
30
15
00
45
45
30
00
00
30
00
0
0
4
3
9
4
4
2
3
.150
.530
.400
.300
.950
.700
.300
.160
.700
4.200
1.900
1.000
0.600
0.930
0.700
0.500K
l.OOOK
l.OOOK
2.400
l.OOOK
l.OOOK
0.132
0.450
0.010K
0.068
0.063
0.040
0.050K
0.050K
0.063
0.050K
0.050K
2.980
3.990
1.380
2.100
2.900
2.670
2.500
0.840
1.150
0.470
0.434
3.500
4.000
1.550
2.400
3.400
2.900
2.700
1.100
1.300
0.570
0.470
0.003
0.003
0.003
0.003
0.003
0.003
0.003
0.003
0.003
0.003
0
0
0
0
0
0
0
0
0
0
.003
.003
.003
.003
.003
.003
.003
.003
.003
.003
K VALUE KNOWN TO tiE
LESS THAN INDICATED
-------
STORET RETRIEVAL DATE 76/03/30
1811CA TF1811CA P002480
39 26 05.0 085 51 50.0 4
FORTVILLE
18 7.5 INGALLS
T/6EIST RESERVOIR 051891
FLATFORK CREEK
11EPALES 2141204
0000 FEET DEPTH CLASS 00
DATE
FROM
TO
73/06/29
73/07/30
73/09/07
73/09/28
73/10/29
73/11/30
73/12/24
74/03/13
74/04/15
74/06/26
74/07/12
74/08/08
00630
TIME DEPTH N02&N03
OF N-TOTAL
DAY FF.ET
10
09
08
08
10
10
08
14
09
09
08
08
30
30
00
30
30
00
00
00
00
00
30
00
MG/L
2.
1.
0.
1.
0.
2.
1.
0.
2.
3.
1.
0.
730
980
510
380
315
900
000
160
160
780
080
800
00625
TOT KJEL
N
MG/L
5.510
6.200
10.300
15.000
16.500
4.700
7.000
6.800
12.000
2.700
3.500
12.000
00610 00671 00665
NH3-N PHOS-DIS PHOS-TOT
TOTAL ORTHO
MG/L
0.120
0.050
0.410
1.440
3.300
0.057
0.048
0.050K
4.100
0.085
0.740
1.250
MG/L P
1.000
1.050
2.020
2.800
2.920
0.590
1.200
0.120
5.800
0.450
1.100
1.350
50051 50053
FLOW CONDUIT
RATE FLOw-MGD
MG/L P INST
1.650
1.750
2.600
3.700
4.300
0.860
1.650
2.400
15.700
0.560
1.350
2.000
0
0
0
0
0
0
0
0
0
0
0
0
MGD MONTHLY
.659
.397
.379
.361
.300
.700
.500
.719
.670
.711
.500
.300
0.500
0.300
0.420
0.400
0.300
0.400
0.500
0.700
0.690
0.689
0.600
0.400
K VALUE KNOWN TO BE
LEbS THAN INDICATED
-------
STORET RETRIEVAL DATE 76/03/30
1811AC TF1B11AC P002300
40 03 10.0 085 32 15.0 4
MIDOLETON
18 7.5 MIOOLETON
T/GEIST RESERVOIR 051991
FALL CREEK
11EPALES 2141204
0000 FEET DEPTH CLASS 00
DATE
FROM
TO
73/06/12
CP(T)-
73/06/12
73/07/10
CP(T)-
73/07/10
73/08/15
73/09/12
CP-
73/09/12
73/10/09
CP-
73/10/09
73/11/12
CP(T)-
73/11/12
73/12/14
7^/01/17
CP
-------
STORET RETRIEVAL DATE 76/03/30
1811AB ASiailAB P002496
40 00 00.0 085 45 00.0 4
PENOLETON
18 7.5 PENOLETON
T/GEIST RESERVOIR 051991
FALL CREEK
11EPALES 2141304
0000 FEET DEPTH CLASS 00
DATE
FROM
TO
73/06/10
CP(T)-
73/06/10
73/07/20
CP(T)-
73/07/20
73/09/20
CP-
73/09/20
73/11/01
CP(T>-
73/11/01
73/12/05
CP(T>-
73/12/05
74/01/04
CPU>-
74/01/04
74/02/05
CP(T>-
74/02/05
74/03/05
CP(T>-
74/03/05
74/04/03
CP(T>-
74/04/03
74/05/08
CP(T)-
74/05/08
74/06/07
CP(T>-
74/06/07
74/07/11
74/08/02
00630
TIME DEPTH N026.N03
OF N-TOTAL
DAY FEET MO/L
06
23
08
20
07
23
07
22
07
22
07
13
07
22
08
23
08
22
08
23
08
22
11
14
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
0
0
0
0
0
0
0
1
0
0
0
0
0
.088
.250
.086
.190
.390
.700
.160
.840
.400
.080
.120
.040
.240
00625
TOT KJEL
N
MG/L
13.200
16.000
10.500
22.000
14.000
12.500
12.000
5.600
6.000
18.000
12.000
9.300
19.000
00610 00671 00665 500S1 50053
NH3-N PHOS-DIS PHOS-TOT FLOW CONDUIT
TOTAL ORTHO RATE FLOW-MOD
MG/L MG/L P MG/L P INST MOD MONTHLY
0
0
3
4
0
0
0
0
0
3
0
0
14
.100
.180
.025
.400
.019
.040K
.920
.050K
.110
.100
.530
.560
.000
2.600
2.260
4.020
3.360
2.500
1.600
2.700
1.050
1.300
2.000
2.100
0.710
3.200
3.300
3.800
5.100
5.100
3.200
2.700
5.500
1.050
1.800
4.300
2.700
1.350
4.400
0.255
0.201
0.176
0.167
0.181
0.173
0.203
0.610
0.570
0.183
0.136
0.170
0.122
0.300
0.208
0.180
0.172
0.172
0.186
0.310
0.287
0.315
0.283
0.188
0.275
0.151
K VALUE KNOWN TO BE
LESS THAN INDICATED
-------
STORE! RETRIEVAL DATE 76/03/30
DATE
FROM
TO
73/06/05
cpm-
73/06/05
73/07/03
CP(T>-
73/07/03
63/11/08
CP(T)-
73/10/09
73/12/18
CP(T)-
73/12/19
74/01/30
cpm-
74/01/30
74/02/27
cpm-
74/02/28
74/07/24
CPU)-
74/07/24
00630 00625 00610 00671
TIME DEPTH N02&N03 TOT KJEL NH3-N PHOS-DIS
OF N-TOTAL N TOTAL ORTHO
DAY FEET MG/L MG/L MG/L MG/L P
08 00
0.820 3.000 0.350 1.680
20 00
08
20
17
05
17
05
06
18
10
10
09
22
00
00
00
00
00
00
00
00
00
00
00
00
0
5
2
2
5
4
.890
.900
.200
.320
.040
.300
1.
980 •
2.300
2.
2.
1.
1.
900
000
700
OOOK
0
0
0
0
0
0
.190
.120
.240
.210
.140
.088
1
.510
2.700
2
3
2
2
.500
.200
.300
.600
1811AA AS1811AA P002300
39 59 00.0 085 46 00.0 4
PENDLETON STATE REFORMATORY
18 7.5 INGALLS
T/GEIST RESERVOIR 051992
FALL CREEK
11EPALES 2141204
0000 FEET DEPTH CLASS 00
00665 50051 50053
PHOS-TOT FLOW CONDUIT
RATE FLOw-MGO
MG/L P INST MGD MONTHLY
2.000 0.300 0.250
1.870 0.200 0.250
3.500 0.500 0.420
3.200 0.350 0.375
4.700 0.330 0.450
2.600 0.350 0.450
3.000 0.400 0.400
K VALUE KNOWN TO dE
LESS THAN INDICATED
------- |