U.S. ENVIRONMENTAL PROTECTION AGENCY
NATIONAL EUTROPHICATION SURVEY
WORKING PAPER SERIES
PACIFIC NORTHWEST ENVIRONMENTAL RESEARCH LABORATORY
An Associate Laboratory of the
NATIONAL ENVIRONMENTAL RESEARCH CENTER - CORVALLIS, OREGON
and
NATIONAL ENVIRONMENTAL RESEARCH CENTER - LAS VEGAS, NEVADA
&GPO 697-032
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REPORT
ON
BERLIN RESERVOIR
WHONING, PORTAGE, AND STARK COUNTIES
OHIO
EPA REGION V
WORKING PAPER No, 395
WITH THE COOPERATION OF THE
OHIO ENVIRONMENTAL PROTECTION AGENCY
AND THE
OHIO NATIONAL GUARD
JUNE, 1975
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CONTENTS
Page
Foreword i i
List of Ohio Study Lakes iv
Lake and Drainage Area Map v
Sections
I. Conclusions 1
II. Lake and Drainage Basin Characteristics 3
III. Lake Water Quality Summary 4
IV. Nutrient Loadings 9
V. Literature Reviewed 14
VI. Appendices . 15
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1i
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 [S303(e)], water
quality criteria/standards review [§303(c)L 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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111
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 Ohio Environmental Protection
Agency for professional involvement, to the Ohio National Guard
for conducting the tributary sampling phase of the Survey, and to
those Ohio wastewater treatment plant operators who provided
effluent samples and flow data.
Ned Williams, Director, and Tom Birch, Ken Carr, Larry
Dietrick, Ron Havlice, Larry Korecko, Rod Mehlhop, Terry Wheeler,
and John Youger, Ohio Environmental Protection Agency, 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 Dana L. Stewart, then the Adjutant General
of Ohio, and Project Officer Lt. Colonel Robert C. Tlnunons,
who directed the volunteer efforts of the Ohio National Guards-
men, are also gratefully acknowledged for their assistance to
the Survey.
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IV
NATIONAL EUTROPHICATION SURVEY
STUDY LAKES
STATE OF OHIO
LAKE NAME
Atwood
Beach City
Berlin
Buckeye
Charles Mill
Deer Creek
Delaware
Dillon
Grand Lake of St.
Grant
Holiday
Hoover
Indian
Loramie
Mosquito Creek
O'Shaughnessy
Pymatuning
Pleasant Hill
Rocky Fork
Shawnee
Tappan
Marys
COUNTY
Carroll, Tuscarawas
Stark, Tuscarawas
Mahoning, Portage, Stark
Fairfield, Licking, Perry
Ashland, Richland
Fayette, Pickaway
Delaware
Muskingum
Auglaize,
Brown
Huron
Delaware,
Logan
Auglaize,
Trumbull
Delaware
Ashtabula, OH; Crawford, PA
Ashland,
Highland
Greene
Harrison
Mercer
Franklin
Shelby
OH; Crawford,
Richland
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^
Ohio /
Map Location
/
Patmos *
BERLIN
FlES ER I/O//?
Damascus J
BERLIN RESERVOIR
Tributary Sampling Site
* Lake Sampling Site
Sewage Treatment Facility
Drainage Area Boundary
9 . ? . 1 ,
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BERLIN RESERVOIR
STORE! NO. 3929
I. CONCLUSIONS
A. Trophic Condition:
Survey data indicate that Berlin Reservoir is eutrophic.
It ranked fourth in overall trophic quality when the 20 Ohio
lakes sampled in 1973 were compared using a combination of
six parameters*. Four lakes had less median total phosphorus,
one had less and one had the same median dissolved phosphorus,
11 had less median inorganic nitrogen, five had less mean chloro-
phyll a^, and five had greater mean Secchi disc transparency.
Survey limnologists did not observe surface algal accumulations
or macrophytes; however, chlorophyll a^ concentrations were con-
sistently high at the various sampling sites.
B. Rate-Limiting Nutrient:
The algal assay results indicate that Berlin Reservoir was
phosphorus limited at the time the assay samples were taken
(04/24/73). These results were substantiated by the lake data;
i.e., the mean inorganic nitrogen to orthophosphorus ratios were
47 to 1 or greater at all sampling times.
C. Nutrient Controllability:
1. Point sources--The phosphorus contribution of known muni-
cipal point sources accounted for 66.9% of the total load reaching
. Berlin Reservoir during the Survey sampling year. The wastewater
* See Appendix A.
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2
treatment plants at Alliance and Sebring contributed 56.2% and
10.8% of the total, respectively.
The phosphorus loading of 5.87 g/m2/yr is over six times that
proposed by Vollenweider (Vollenweider and Dillon, 1974) as a
eutrophic loading (see page 13). For this reason, all phosphorus
inputs should be minimized to the greatest practicable extent.
A 100% reduction of phosphorus from the municipal point sources
would lower the loading to 1.94 g/m2/yr. If attainable, this
degree of reduction should at least slow the rate of eutrophication
of the reservoir. The relatively short hydraulic retention time
of 81 days would facilitate improvement of water quality after
phosphorus controls are initiated.
2. Non-point sources—During the sampling year, the phosphorus
contribution of non-point sources, excluding precipitation,
accounted for 32.4% of the total load to the lake. The Mahoning
River contributed 14.4%, Beech Creek contributed 2.6% the Deer
Creek Reservoir outlet contributed 2.5%, and the remaining three
tributaries collectively contributed 3.6% of the total load.
Ungaged tributaries were estimated to have contributed 9.3% of
the total.
The phosphorus export rate of Island Creek was appreciably
higher than the rates of the other Berlin Reservoir tributaries
(see page 13). However, there are no known point sources impacting
Island Creek, and the higher export rate may be the result of dif-
fering land-use practices.
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II. LAKE AND DRAINAGE BASIN CHARACTERISTICS1"
A. Lake Morphometry :
1. Surface area: 8.90 kilometers2.
2. Mean depth: 4.9 meters.
3. Maximum depth: >14.0 meters.
4. Volume: 43.610 x 10s m3.
5. Mean hydraulic retention time: 81 days (based on outlet flow),
B. Tributary and Outlet:
(See Appendix C for flow data)
1. Tributaries -
Drainage Mean flow
Name area (km2)* (m3/sec)*
Mahoning River 231.0 2.2
Mills Creek 49.5 0.5
Island Creek 15.3 0.2
Beech Creek 49.2 0.5
Deer Creek Res. outlet 98.4 1.0
Willow Creek 16.8 0.2
Minor tributaries &
Immediate drainage - 173.2 1.8
Totals ' 633.4 6.4
2. Outlet -
Mahoning River 642.3** 6.2
C. Precipitation***:
1. Year of sampling: 96.4 centimeters.
2. Mean annual: 91.3 centimeters.
t Table of metric equivalents—Appendix B.
ft Youger, 1975.
* For limits of accuracy, see Working Paper No. 175, "...Survey Methods,
1973-1976".
** Includes area of lake.
*** See Working Paper No. 175.
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4
III. LAKE WATER QUALITY SUMMARY
Berlin Reservoir was sampled three times during the open-water season
of 1973 by means of a pontoon-equipped Huey helicopter. Samples for
physical and chemical parameters were collected from a number of depths
at seven lake stations in the spring, four stations in the summer, and
five stations in the fall (see map, page v). During each visit, a single
depth-integrated (4.6 m or near bottom to surface) sample was composited
from the sampled stations for phytoplankton identification and enumeration;
and during the first visit, two 18.9-liter depth-integrated samples were
composited for algal assays (stations 1, 2, 3, and 4 were combined, and
stations 5, 6, and 7 were combined). Also each time, a depth-integrated
sample was collected from each of the stations for chlorophyll a_ analysis.
The maximum depths sampled were 7.6 meters at station 1, 14.0 meters at
station 2, 7.6 meters at station 3, 4,6 meters at station 4, 8.8 meters
at station 5, 3.0 meters at station 6, and 1.5 meters at station 7.
The sampling results are presented in full in Appendix D and are
summarized in the following table. During the April sampling visit,
replicate samples were taken for quality control purposes. For comparison
of these results and differences in the various parameters at the other
sampling times, refer to Appendix D.
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PARAMETER
TEMP (o
otss OXY
CNDCTVY (HCHOMO)
PH (STAND UNITS)
TOT ALK (MG/L)
TOT P (MG/L)
ORTKO P (MG/L>
N02»N03 (MG/LI
AMMONIA (MG/L)
KJEL N IMG/L)
INORG N (MG/LJ
TOTAL N (MG/L)
CHLRPYL A
SECCM] (METEWS)
A. SUMMARY OF PHYSICAL ANO
1ST SAMPLING ( 4/24/73)
7 SITES
CHEMICAL CHARACTERISTICS FOR BERLIN RESERVOIR
STO«ET CODE 3929
2ND SAMPLING I 7/30/73)
it SITES
3RD SAMPLING (ID/ 8/73)
5 SITES
RANGE
10.0
6.4
360.
7.1
27.
0.024
0.003
0.590
0.030
0.500
0.630
1.320
10.1
0.6
- 17.2
- 11.8
- 440.
8.5
82.
- 0.238
- 0.070
- 1.100
- 0.220
- 1.200
- 1.170
- 2.130
- 32.8
1.3
MEAN
13.5
9.6
390.
7.9
62.
0.066
0.019
0.008
0.087
0.769
0.974
1.657
16.3
0.9
MEDIAN
13.3
9.7
385.
7.9
61.
0.042
0.006
0.890
0.070
0.700
0.975
1.615
14,7
0.9
RANGE
23.6
1.4
396.
7.2
76.
0.026
0.00?
0.140
0.080
0.500
0.320
0.7SO
5.4
0.5
- 24.8
7.3
- 534.
9.3
- 120.
- 0.221
- 0.034
- 0.690
* 0.600
- 1.600
- 1.490
- 2.490
- 15.7
1.0
MEAN
24.4
5.3
434.
7.9
B6.
0.056
0.007
0.306
0.166
0.893
0.492
1.199
11.5
0.8
MEDIAN
24.4
S.S
413.
7.7
ao.
0.033
0.003
0.235
0.130
o.eoo
0.365
1.060
12.4
0.9
RANGE
18.4
3.8
402.
7.5
00.
0.038
0.005
0.200
0.040
0.400
0.270
0.660
6.0
0.5
- 19.7
9.8
- 574.
8.2
- 113.
- 0.126
- 0.011
- 0.320
- 0.280
- 2.300
- 0.560
- 2.580
- 52. 5
1.0
MEAN
18.9
6.1
431.
7.7
89.
0.059
0.007
0.256
0.072
0.823
0.328
1.079
16.5
0.8
MEDIAN
ia. a
s.8
422.
7.6
88.
0.048
0.007
0.260
0.050
0.700
0.300
0.960
7.8
0.9
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B. Biological characteristics:
1. Phytoplankton -
Sampling
Date
04/24/73
07/30/73
10/08/73
2. Chlorophyll a_ -
Sampling
Date
04/24/73
Dominant
Genera
1.
2.
3.
4.
5.
1.
2.
3.
4.
5.
1.
2.
3.
4.
5.
Melosira sp.
Flagellates
Cryptomonas sp.
Nitzschia sp.
Synedra sp.
Other genera
Total
Centric diatoms
Flagellates
Melosira s_p_.
Pennate diatoms
Cryptomonas sj3.
Other genera
Total
Flagellates
Merismopedia sp,
Raphidiopsis sj>,
Scenedesmus sp.
Cryptomonas sp.
Other genera
Total
Station
Number
01
02
03
04
05
06
07
Algal Units
per ml
1,768
1,681
1,092
445
273
1,034
6,293
1,169
627
576
322
237
1.236
4,167
11,346
Chlorophyll a_
13.3
14.7
10.1
22.8
14.3
17.0
22.0
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c.
Sampling
Date
07/30/73
10/08/73
Station
Number
01
02
03
04
05
06
01
02
03
04
05
Chlorophyll a
(ug/D
5.4
12.2
12.7
15.7
6.3
6.0
7.8
10.1
52.5
Limiting Nutrient Study:
1. Autoclaved, fil
a. Stations 1,
Spike (mg/1)
Control
0.050 P
0.050 P + 1.0 N
1.0 N
b. Stations 5,
Spike (mg/1)
Control
0.050 P
0.050 P + 1.0 N
1.0 N
2. Discussion -
The control
tered, and nutrient spiked -
2, 3, and 4 -
Ortho P
Cone, (mg/1)
0.016
0.066
0.066
0.016
6, and 7 -
Ortho P
Cone. Cmg/1)
0.052
0.102
0.102
0.052
yields of the
Inorganic N
Cone, (mg/1)
1.004
1.004
2.004
2.004
Inorganic N
Cone, (mg/1)
0.984
0.984
1.984
1.984
Maximum yield
(mgyi-dry wt.)
2.7
16.7
20.4
2.8
Maximum yield
(mg/1 -dry wt.J^
15.0
20.3
27.8
17.6
assay alga, Selenastrum capri-
cornutum, indicate that the potential primary productivity
of Berlin Reservoir at stations 1, 2, 3, and 4 (composited)
was moderate but was quite high at stations 5, 6, and 7 (com-
posited) at the time of sample collection (04/24/73). The
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8
control yield of the stations 5-7 sample was over five times
the control yield of the stations 1-4 sample. The high phos-
phorus levels and high control yield from stations 5-7 are
indicative of the proximity of nutrient point sources upstream
of these stations.
The algal assay results also indicate that Berlin Reservoir
was phosphorus limited at the time the samples were collected.
Note the lack of a significant increase in the yields when
nitrogen alone was added; but with the addition of phosphorus
alone, the yields increased significantly.
The lake data also indicate phosphorus limitation for the
reservoir at the time of sample collection (April, 1973) as
well as the July and October, 1973, samplings. The mean
inorganic nitrogen to orthophosphorus ratios were 47 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 Ohio 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 May, 1973, and was completed in April, 1974.
Through an interagency agreement, stream flow estimates for the year
of sampling and a "normalized" or average year were provided by the Ohio
District Office of the U.S. Geological Survey for the tributary sites
nearest the lake.
In this report, nutrient loads for sampled tributaries were deter-
mined by using a modification of a U.S. Geological Survey computer program
for calculating stream loadings*. Nutrient loads shown are those measured
minus point-source loads, if any.
Nutrient loads for unsampled "minor tributaries and immediate drainage"
("II" of U.S.G.S.) were estimated using the means of the nutrient loads,
in kg/km2/year, at stations B-l, C-l, D-l, and F-l and multiplying the
means by the II area in km2.
The operator of the Alliance wastewater treatment plant provided
monthly effluent samples and corresponding flow data. However, the com-
munity of Sebring did not participate in the Survey, and nutrient loads
were estimated at 1.134 kg P and 3.401 kg N/capita/year.
* See Working Paper No. 175.
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10
A. Waste Sources:
1. Known municipal -
Name
Alliance*
Sebring**
Pop.
Served
30,000
4,954
Treatment
trickling
filter
trickling
filter
Mean Flow
(rnVd)
11,705.6
1,875.1
Receiving
Water
Ma honing
River
Sebring Branch
of Mahoning R
2. Known industrial - None
* Graybill, 1973; more than 25% of the total load to this plant is contributed
by industry.
** Anonymous, 1971 (population shown is 1970 Census; flow shown is estimated
at 0.3785 m3/capita/day).
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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) -
Mahoning River 7,530 14.4
Mills Creek 840 1.6
Island Creek 815 1.6
Beech Creek 1,375 2.6
Deer Creek Res. outlet . 1,295 2.5
Willow Creek 235 0.4
b. Minor tributaries & immediate
drainage (non-point load) - 4,850 9.3
c. Known municipal STP's -
Alliance 29,370 56.2
Sebring 5,620 10.8
d. Septic tanks* - 180 0.3
e. Known industrial - None
f. Direct precipitation** - 155 0.3
Total 52,265 100.0
2. Outputs -
Lake outlet - Mahoning River 12,595
3. Net annual P accumulation - 39,670 kg.
* Estimate based on 624 lakeshore dwellings and one park; 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) -
Mahoning River 155,770 29.3
Mills Creek 41,730 7.9
Island Creek 14,035 2.6
Beech Creek 35,620 6.7
Deer Creek Res. outlet 53,835 10.1
Willow Creek 6,420 1.2
b. Minor tributaries & inmediate
drainage (non-point load) - 124,010 23.3
c. Known municipal STP's -
Alliance 67,020 12.6
Sebring 16,850 3.2
d. Septic tanks* - 6,685 1.3
e. Known industrial - None
f. Direct precipitation** - 9,610 1.8
Total 531,585 100.0
2. Outputs -
Lake outlet - Mahoning River 394,940
3. Net annual N accumulation - 136,645 kg.
* Estimate based on 624 lakeshore dwellings and one park; see Working
Paper No. 175.
** See Working Paper No. 175.
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13
D. Mean Annual Non-point Nutrient Export by Subdrainage Area:
Tributary kg P/km2/yr kg N/km2/tyr
Mahoning River 33 674
Mills Creek 17 843
Island Creek 53 917
Beech Creek 28 724
Deer Creek Res. outlet 13 547
Willow Creek 14 382
E. Yearly Loadings:
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 oligo-
trophic if morphometry permitted. A mesotrophic 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 5.87 4.46 59.7 15.4
Vollenweider phosphorus loadings
(g/mz/yr) based on mean depth and mean
hydraulic retention time of Berlin Reservoir:
"Dangerous" (eutrophic loading) 0.90
"Permissible" (oligotrophic loading) 0.45
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14
LITERATURE REVIEWED
Anonymous, 1971. Inventory of municipal waste facilities. EPA
Publ. OWP-1, vol. 5, Wash., DC.
Graybill, B. R. (operator), 1973. Treatment plant questionnaire
(Alliance STP). Alliance, OH.
Vollenweider, R. A., and P. J. Dillon, 1974. The application of the
phosphorus loading concept to eutrophlcation research. Natl. Res.
Council of Canada Publ. #13690, Canada Centre for Inland Waters,
Burlington, Ontario.
Youger, John, 1975. Personal conmunication (lake morphometry). OH
Env. Prot. Agency, Columbus.
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VI. APPENDICES
15
APPENDIX A
LAKE RANKINGS
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LAKES RANKED BY INDE* NOS.
LAKE CODE LAKE NAME
NO
2 3-J21
3 3924
4 3929
5 3914
6 313*.
7 3^27
a 3932
9 390fo
10 3901
11 3915
12 3907
13 3->12
14 3^33
15 3930
16 3905
17 3902
18 3908
19 3917
20 3931
AT*OOD
MOSUUITO CREEK SESirtVOlR 483
PLEASANT HILL LAKE 431
dE^LlN RESERVOIR 429
HOOVER HESErtVOIK 39?
TAPPAN LAKE 381
LAi^E SAINT MARYS 297
ROCKY FORK LAKE 292
DEER CPEEK KESESvOIR ?90
BEACH CITf KfcSERVOIR 277
IN01AN LAKE ?6b
DELAWARE RESERVOIR 263
GRANT LAKE 261
SHA*NEE LAKE ?49
HOLIDAY LAKE 220
CHARLES MILL RESERVOIR 216
bUCKEYE LAKE 207
UILLION RESEHVOm 206
LORAMIE LAKE 178
O'SHAUGNESSY RESERVOIK 173
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PERCENT OF LAKES WITrt HIGHER VALUES (NUMBEK OF LAKEb *ITH HIGHER VALUES)
LAKE
CODE LAKE NAME
3901 BEACH CITr RESERVOIR
3902 8UCKEYE LAKE
3905 CHARLES MILL RESEHVOIR
390b DEE** CREEK HESEKVOIR
3907 DELAWARE RESERVOIR
3908 OILLION RESERVOIH
3912 GRANT LAKE
3914 HOOVER RESERVOIR
3915 INDIAN LAKE
3917 LORAM1E LAKE
3921 MOSQUITO CREEK «ESERVOI*
3924 PLEASANT HILL LAKE
3927 LAKE SAINT MAKYS
3928 ATrfOOD RESERVOIR
3929 BEKLIN HESERVOIK
3930 HOLIDAY LAKE
3V31 O'SHAUGNESSY
3932 ROCKY FORK LAKE
3933 SHAWNEE LAKE
3934 TAPPAN LAKE
MEDIAN
TOTAL P
37 <
11 (
26 <
53 (
58 (
16 <
47 (
87 (
42 (
5 (
7* (
95 (
21 (
100 (
79 (
32 (
0 (
68 (
63 (
87 (
7)
21
S>
10)
11)
3)
9)
16)
81
1)
14)
18)
4)
19)
15)
to)
0)
13)
12)
161
MEDIAN
INOrtG N
21
76
63
5
16
32
58
26
76
37
100
68
95
89
42
53
0
47
11
B4
( 4>
( 14)
I 12)
< i)
( 3)
( 6)
< 11)
( 5)
( 14)
( 7)
< 19)
I 13)
( 18)
< 17)
( 6)
< 10)
< 0)
< 9)
( 2)
( 16)
500-
MEAN SEC
11 <
5 <
37 (
63 <
J2 1
42 <
16 <
69 (
21 <
0 (
A2 (
100 <
26 (
95 (
74 <
62 <
47 <
50 <
53 <
68 (
2)
1)
7)
12)
6)
8)
3)
17)
4)
0)
IS)
19)
S)
18)
14)
15)
9)
11)
10)
13)
MEAN
CrtLOHA
84 (
0 (
21 (
95 (
89 (
58 <
32 (
79 <
16 (
5 (
53 <
63 <
11 (
68 (
74 <
26 <
100 (
42 (
37 (
47 (
16>
0)
**>.
IB)
17)
ID
6)
IS)
3)
1)
10)
12)
2)
13)
14)
S)
19)
8)
71
9)
Ib-
MIN DO
82 t
89 (
11 <
63 <
47 <
53 (
74 <
32 (
58 (
97 (
82 (
39 <
97 (
39 (
68 (
11 <
26 (
11 (
11 (
11 (
15)
17)
0>
12)
9)
10)
14)
6)
ID
18)
15)
7»
18)
7)
13>
0)
5)
0)
0)
0)
MEDIAN
DISS OrtTriO P
42 (
26 (
58 I
11 (
21 <
5 <
34 <
79 <
53 (
34 (
92 (
66 (
47 <
100 <
92 1
16 (
0 <
66 <
74 (
84 (
8)
S)
11)
2)
4)
1)
6)
IS)
10)
6)
17)
12)
9)
19)
17)
3)
0)
12)
14)
It.)
INDEX
NU
277
207
216
240
263
206
261
392
266
178
483
431
297
491
429
220
173
2V2
249
3B1
-------
LAKE DATA TO BE USED IN RANKINGS
LAKE
CODE LAKE NAME
3901 BEACH CITY RESERVOIR
3902 BUCKEYE LAKE
3905 CHARLES HILL RESERVOIR
3906 DEER CREEK RESERVOIR
3907 DELAWARE RESERVOIR
3908 OILLION RESERVOIR
3912 GRANT LAKE
3914 HOOVER RESERVOIR
391S INDIAN LAKE
3917 LORAM1E LAKE
3921 M05CIUITO CREE* RESERVOIR
3924 PLEASANT HILL LAKE
3927 LAKE SAINT MARYS
3928 ATKUOO RESERVOIR
3929 BERLIN RESERVOIK
3930 HOLIDAY LAKE
3931 O'SHAUGNESSY RESERVOIR
3932 ROCKY FORK LAKE
3933 SHAWNEE LAKE
3934 TAPPAN LAKE
MEDIAN
TOTAL P
0.122
0.179
0.127
0.098
0.086
0.163
0.113
0.040
0.120
0.185
O.ObS
0.036
0.143
0.031
0.042
0.125
0.208
0.067
0.069
0.040
MEDIAN
INORG N
1.990
0.380
0.465
2.980
2.340
1.590
0.570
1.640
0.380
1.380
0.150
0.455
0.200
0.205
0.900
0.575
3.070
0.790
2.380
0.280
500-
MEAN SEC
489.000
49U.OOO
482.555
470.125
484.111
481.250
486.333
462.750
485.222
494.000
465.333
456. 83J
484.167
462.000
465.435
465.333
479.333
473.000
474.333
466.111
MEAN
CHLOKA
10.867
186. S67
67.144
9.887
10.856
27.400
40.533
13.017
76.855
104.100
36.267
22.850
79.150
16.442
15.496
55.350
S.522
38.022
39.567
37.711
15-
MIN DO
11.600
9.600
15.000
13.900
14.500
14.300
12.200
14.800
14.200
8.200
11.600
14.700
8.200
14.700
13.600
15.000
14.900
15.000
15.000
15.006
MEDIAN
OISS ORTHO P
O.Olb
0.020
0.011
0.036
0.024
0.037
0.019
0.008
0.012
0.019
0.006
0.010
0.014
o.oos
0.006
0.034
0.159
0.010
0.009
0.007
-------
APPENDIX B
CONVERSIONS 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
-------
TrtlBUTAKY FLO* INFORMATION FOk OHIO
1/27/75
LAKE CODE 3929
bEKLIN rttiERVUIS
TOTAL DRAINAGE AKEA OF LAKEtSO KM)
SUM-UKftlNA&£
TRIBUTARY AREAtSU KM)
NORMALIZED FLOWS
3929A1
3929A2
3929ril
3929C1
3929D1
3929tl
3929F1
3929ZZ
231.0
lb.3
98.4
in. a
1B2.1
JAN
6. Ufa
3.4H
0.74
U.23
0.74
1.50
0.26
2.dO
Ft*
9.1?
4.42
0.96
0.29
0.91
1.78
0.31
3.26
MAR
9.57
5.64
1.22
0.40
1.22
2. 36
0.4?
4.36
AHR
5.92
4. US
0.88
0.31
0.99
1.93
0.34
3.51
HAY
6.60
2.86
0.65
O.ltt
0.57
1.13
0.20
2.U7
JUN
6.71
1.39
0.24
0.10
0.31
0.65
0.11
1.25
JOL
7.36
O.ttd
0.19
0.06
0.20
0.4(1
0.07
0.76
AUG
7.J9
0.66
0.09
0.03
0.11
0.24
0.04
0.45
SEP
5.78
0.31
0.04
0.02
O.Oti
0.17
0.03
0.34
OCT
3.74
0.62
0.12
0.03
0.09
0.19
0.03
0.37
NOV
2.32
0.82
0.15
0.06
0.20
0.42
0.07
0.79
DEC
4. 08
1.93
0.42
0.13
0.42
0.65
O.lb
1.61
MEAM
6.21
2.24
0.47
0.15
0.48
0.97
0.17
1.79
SUMMAKY
OFAL
iUM UF
DRAINAGE
AREA OF LAKE =
SOd-O^AINAtt ASEAS =
642.3
642.3
TOTAL FLO*
TOTAL FLOW
IN -
our =
75.71
74.64
MEAN MONTHLY FLOWS ANJ LJAILY FLOWS (CMS!
TRIBUTARY MONTH YEAH
3929A1
MEAN FLOW DAY
FLO* DAY
PLOW DAY
FLOW
3929A2
5
6
7
rt
9
10
11
12
1
2
3
4
5
6
7
8
9
10
1 1
12
1
2
3
«*
73
73
VJ
73
73
7J
7J
73
74
74
74
74
73
73
U
73
73
/J
7J
73
ft
74
74
74
16.25
5.10
5.52
6.63
7.16
2.15
2.52
8.95
12.40
6. we
19.57
13.22
4.76
2.36
0.96
1.19
0.51
1.19
2.75
4.19
6.12
2.63
9.15
4.39
5
J
22
16
29
20
4
2
6
3
3
7
5
3
22
16
39
20
4
2
6
3
3
7
17.70
3.3-*
5.30
6.99
b.32
1.76
1.76
12.57
16.57
23.05
2.69
2^.73
2.30
1.93
2.92
2,89
1.03
1.J2
2. 29
J.73
2.15
6.71
4.16
15
16
15
16
4.73
29.73
2.U7
10.00
-------
FLO« INFORMATION Fok OHIO
1/27/7S
LAr(E CODE 3929
MEAN MONTHLY FLOWS AND UAILY FLOrfS(CHil
THldUTSMY MONTH YLA^ MEAN FLOW DAY
3929bl
3929CI
5
6
7
a
9
10
11
12
1
2
3
5
6
7
8
9
10
11
12
1
2
3
S
6
7
%
9
10
11
12
1
I
3
i.
b
6
7
a
q>
10
11
12
1
g
3
4
73
73
73
73
73
73
73
73
74
74
74
73
73
73
73
73
73
73
73
74
74
74
73
73
73
73
73
73
73
73
74
74
74
74
73
73
73
73
73
73
73
73
74
74
ft
Y4
1.44
0.24
0.19
0. 16
0.06
0.14
U.24
0.62
1.13
0.48
1.9b
0.74
0.40
O.U9
0.06
0,06
0.04
0.03
0.39
0.19
0.37
U.14
0.62
0.26
1.25
0.31
O.?ti
0.19
0.13
0.1(1
0.31
O.oZ
1.13
0.45
1.95
O.rt2
2.49
0.65
0.40
0.40
0.27
0.21
O.bb
1.22
2.32
O.BB
3.79
i.by
5
3
22
IB
2V
2u
4
2
6
3
3
7
5
3
22
18
29
20
4
2
6
3
3
7
S
3
22
lb
29
20
4
2
b
3
3
7
5
3
22
16
29
20
4
2
6
3
3
7
FLOW
FLO* DAY
FLU*
0.1V
0.1H
0.40
0.13
0.12
0.14
0.34
0. jt
0.4U
1.44
0.51
0.15
o.oa
0.06
U.14
o.oa
0.02
0.05
o.iu
0.10
0.12
U.45
O.lfc
0.4d
u.25
0.19
0.26
o.oa
o.ia
0.34
0.34
0.4J
1.42
0.93
0.54
0.37
0.9&
0.0
0.0
0.0
0.0
O.t)
0.79
2.H6
1.4)2
15
lb
15
16
15
lb
lb
16
0.31
2.15
0.10
0.65
0.31
2.12
4.25
-------
FLO* INFORMATION FOR OHIO
1/27/75
LAKE CODE 39?9
BEWLIN KEbLHVOIR
MEAN MONTHLY FLOWS ANu UAlLY FLOWS
TRIBUTARY
3929F1
3929ZZ
MONTH
YtMK
5
6
7
8
9
10
11
12
1
2
3
4
5
6
7
8
9
10
11
12
I
2
3
4
73
73
73
73
73
73
73
73
7*
7<*
7t
74
73
73
73
73
73
73
73
73
74
74
74
74
FLOW DAY
0.42
0.10
0.07
0.07
0.04
0.03
0.10
0.22
0.40
U.15
0.68
U.2B
4.56
1.22
0.74
0.76
0.54
0.40
1.22
2.32
4.3f>
1.61
t.97
2.92
5
3
22
Ifa
29
20
4
2
b
3
3
7
FLUW UAY
FLOW UAY
FLOW
0.16
U.06
0.07
0.16
0.09
U, i j
. y J
0.0&
0.12
0.12
0.13
0.48
0.17
IS
16
0.11
0.74
-------
APPENDIX D
PHYSICAL and CHEMICAL DATA
-------
STOKET RETRIEVAL OAlE 75/U1/27
3^2901
41 02 37.0 031 00 16.0
3^133 OHIO
OATt
FROM
TO
73/04/24
73/u?/3U
73/10/OtJ
UATE
FrtOM
TO
73/U4/24
73/U7/30
73/10/08
TIME DEPTH
OF
UAf FEtT
09 25 0000
09 25 OOOJi
y y ^^ u 0 1 i
09 ?b 0025
09 35 OOOU
09 35 0008
09 35 0015
09 35 0025
10 25 0000
10 25 OOOb
10 25 0012
1 7 35 0000
17 35 0015
17 35 0025
TIME DEPTH
OK
DAY FEET
09 25 0000
09 ?5 0008
09 25 0015
09 25 0025
09 35 0000
10 25 0000
10 25 0005
10 25 0012
17 35 JOOO
17 35 0015
17 35 0025
OJOlO
wuTEK
TEMfJ
CtNT
13.3
11.0
14.0
12.4
24.6
24.4
24."*
19.7
19. 0
18. 1
00665
PHOb-Tor
MG/L P
U.041
•J.032
0.034
0.025
0.027
0.02(5
u.028
ij.OnO
U.038
J.044
00300
00
MG/L
10.4
10.0
10.2
b.4
5.5
h.H
5.8
5.8
32217
Chi_wpnrL
A
OG/L
13.3
13. i
5.4
6.3
00077 00094
TWANSP CNDUCr\/Y
bECCHl F1ELU
M1CKOMHO
bO
50
36
37
400
390
390
380
400
380
385
39b
396
396
409
404
402
HEPALtS
3
00400
PH
SO
a. 20
H.20
B.OJ
7. BO
8.20
8.10
8.00
7.8J
7,8u
7. 70
7.70
7.60
7.50
7.50
00-tJU
T ALK
CAC03
MG/L
38
60
60
61
79
79
78
SO
d3
88
2111302
0026
00610
NHJ-N
TOTAL
HG/L
0.060
0.070
0.080
0.070
0.090
0.060
0.100
0.040
U.040
0.0 SO
FEET UEfTH
00625
TOT KJEL
N
HG/L
1.100
0.600
0.600
0.500
0.600
0.600
0.500
0.700
0.400
0.400
00630
N02b,N03
N- TOTAL
HG/L
0.890
0.960
1.000
1.100
0.280
0.26U
0.2BO
0.260
0.260
0.270
00671
PHOS-OIS
OBTriO
HC/L P
0.009
0.006
0.005
0.004
0.003
0.002ft
0.002ft
0.006
0.006
0.006
K V,;L
LEbS
Tu
-------
STORET RETRIEVAL DATE 75/01/37
392902
41 01 09.0 OBI 00
d£HLlN RESERVOIR
39099 OHIO
DATE
FROM
TO
73/04/24
73/07/30
73/10/Ott
OU010
TIME DEPTH WATER
OF TEMP
DAY FEET
10
10
10
10
10
10
10
10
10
10
10
10
11
11
11
11
17
17
17
17
15
15
15
15
15
15
25
25
25
25
25
25
50
50
50
50
10
10
10
10
0000
0008
0015
0020
0035
0046
0000
0008
0015
0020
0035
0046
0000
0005
0015
0025
0000
0015
0027
0036
CENT
13.
13.
12.
11.
10.
10.
24.
24.
24.
24.
19.
IB.
IS.
18.
7
2
7
6
4
0
8
7
4
2
7
7
S
4
00300
00
MG/L
10
10
9
9
8
7
5
6
6
5
4
3
.8
.0
.8
.1
.6
.3
.8
.1
.6
.8
.2
.8
00077 00094
TRANSP CNDUCTVY
SECCHI FIELD
INCHES MICROMHO
37
37
38
30
385
380
380
380
380
380
385
380
380
380
380
385
404
407
405
407
413
421
420
422
11EPALES
3
00400
PH
SU
a. 20
6.20
e.oo
7.90
7.80
7.70
8.20
.{J.20
H.OO
7.90
7.80
7.70
6.10
7.90
7.70
7.70
7.70
7.60
7.50
7.50
00410
T ALK
CAC03
MG/L
60
61
28
28
27
62
76
78
76
77
HS
87
B5
66
2111202
0050
00610
NH3-N
TOTAL
MG/L
0.040
0.050
0.060
0.100
0.120
0.170
0.090
0.100
0.130
0.140
0.040
0.060
0.060
0.100
FEET DEPTH
00625
TOT KJEL
N
MG/L
0.800
0.700
0.600
0.600
0.600
0.700
0.900
0.800
0.800
0.800
0.600
0.600
0.700
0.800
00630
N02&N03
N-TOTAL
MG/L
0.890
0.930
0.940
0.980
0.980
1.000
0.240
0.220
0.230
0.220
0.240
0.260
0.290
0.320
00671
PHOS-D1S
ORTMO
MG/L P
0.006
0.005
0.009
O.OOS
0.007
0.009
0.003
0.002
0.002
0.003
0.006
0.008
0.009
0.010
-------
STORE! KETKIEVAL UATt 7^/01/27
DATE
FKOM
TO
73/0^/2^
73/07/30
73/10/08
OU66S 32217
TIME OE^TH PHOS-TOT CHLRPi-iVL
OF A
UAY FEET Mb/L P 00/L
10
10
10
10
10
10
10
11
11
11
11
17
17
17
17
15
15
15
15
15
15
25
50
50
50
50
10
10
10
10
0000
0008
UOiD
0020
003b
(J046
0000
0000
OOOb
0015
0025
OOUO
0015
0027
0036
J
(j
0
0
0
u
0
0
K
U
0
(j
u
0
.034
.031
.026
.033
.031
.032
.027
.029
.02d
.033
.OM
.0^*2
.Obl
.102
I'*.?
It. 7
12.2
6.0
01 0^.0 081 00 02.0
tbEH
OHIO
HtHALhS
j
2111gy2
FEET DEPTH
-------
STOKET RETRIEVAL DATE 75/01/87
392903
41 00 18.0 081 00 10.0
HEHLIN RESERVOIR
3*133 OHIO
00010
DATE TIME DEPTH WATER
FROM OF TEMP
TO DAV FEET CENT
73/04/24 11 10 0000 13.4
11 10 0007 13.2
11 10 0015 12.7
11 10 0025
11 20 0000
11 20 0007
11 20 0015
11 20 0025 10.9
73/10/08 16 40 0000 Itt.b
16 40 0010 18.6
16 40 0018 18.5
11EPALES
00300
DO
MG/L
1C. 4
9.7
9.1
6.4
6.0
5.6
00077
TRANSP
SECCHl
INCHES
40
40
38
00094
CNOUCTVY
FIELD
MICKOMHO
360
380
380
360
375
380
380
365
423
425
433
3
00400
PH
SU
7.90
7.70
7.60
00410
T ALK
CAC03
Mli/L
62
61
60
61
88
90
91
2111202
0028
00610
NH3-N
TOTAL
MG/L
0.050
0.040
0.050
0.100
0.040
0.060
0.080
FEET DEPTH
00625
TOT KJEL
N
MG/L
0.600
0.700
0.600
0.600
1.000
0.600
0.700
00630
N02&N03
N-TOTAL
MG/L
0.840
0.890
0.920
0.870
0.230
0.230
0.200
00671
PHOS-DIS
OHTHO
MG/L P
0.005
0.004
0.004
0.005
0.011
0.005
0.005
00665 32217
DATE TIME DEPTH PHOS-TUT CHLRPHYL
FROM OF A
TO DAY FEET MG/L H UG/L
73/04/24 11 10 0000 0.027 10.1
11 10 0007 U.024
11 10 0015 0.025
11 10 0025 0.027
11 20 0000 13.3
73/10/08 16 40 0000 0.063 7.8
16 40 0010 O.U45
16 40 0018 0.056
-------
iTOKET RETRIEVAL DATE 75/01/27
39290**
40 59 45.0 081 00 48.0
BERLIN KESEKV01R
39133 OHIO
DATt
FHOM
TO
73/04/24
73/10/08
DATt
FROM
TO
73/04/24
73/10/08
TIME DEPTH
OF
DAY FEET
13 35 0000
13 35 0008
13 35 UOlb
13 45 0000
13 45 0008
13 45 0015
16 20 0000
16 ?0 0008
TIME OEpTH
OF
CJAY FEET
13 35 0000
13 3S OOOtt
13 35 00 IS
13 45 0000
13 45 0008
13 45 0015
16 20 OUdO
16 20 0008
00010
WATER
TEMP
CENT
14.5
13.6
12.9
19.3
18.7
00665
PHOS-TOT
MG/L P
0.043
0.061
0.041
U.K49
0.057
0.042
0.055
u.048
00300
00
MG/L
11.8
11.0
6.8
5.8
32217
CHLRPHYL
A
UG/L
22.8
22.6
10.1
00077 00094
THANSP CNDUCTVV
SECCHI FIELD
INCHES MICKOMHO
36 380
390
390
36 380
385
390
36 427
426
11EPALES 2111202
3 0018 FEET DEPTH
00400 00410 00610 00625 00630
PH
T ALK NH3-N
CAC03 TOTAL
bU
8
a
8
8
a
8
8
7
MG/L MG/L
.50
.30
.20
.50
.40
.20
.20
.90
63 0
61 0
61 0
61 0
60 0
60 0
90 0
88 0
.040
.040
.050
.040
.040
.050
.ObO
.040
TOT KJEL
N
MG/L
0.900
1.000
0.700
1.000
0.900
0.700
1.100
0.800
N02&N03
N- TOTAL
MG/L
0.860
0.860
0.890
0.850
0.870
0.900
0.220
0.270
00671
PHOS-UIS
Oft T HO
MG/L P
0.006
0.006
0.004
0.006
0.005
0.005
0.007
0.007
-------
STORET RETRIEVAL DATE 75/01/37
392905
41 00 15.0 081 03 S5.0
HtHLIN RESERVOIR
39133 OHIO
DATE
FROM
TO
73/04/24
73/07/30
73/10/08
DATE
FROM
TO
73/04/24
73/07/30
73/10/08
TIME DEPTH
OF
DAY FEET
16 10 0000
16 10 0007
16 10 0010
16 20 0000
16 20 0007
16 20 0010
11 25 0000
11 25 0005
11 25 0015
11 25 0029
16 10 0000
TIHE DEPTH
OF
DAY FEET
16 10 0000
lb 10 0007
16 10 0010
16 20 0000
16 20 0007
16 20 0010
11 25 0000
11 25 0005
11 25 0015
11 25 0029
Ib 10 0000
00010
WATER
TEMP
CtNT
16.1
14.2
12.9
24.7
24.7
24.2
23.6
19.5
00665
PHOS-TOT
MG/L P
J. 031
0.051
0.046
0.042
0.053
U.051
0.044
0.0*4
U.OJ3
0.042
0.126
00300
00
MG/L
9.5
8.9
7.0
4.7
1.4
9.8
32217
CMLKPHYL
A
UG/L
14.3
13.2
12.7
52.5
00077 00094
TRANSP CNDUCTVY
5ECCHI FIELD
INCHES MICROHHO
35 395
395
415
35 395
400
410
36 420
420
419
430
20 574
11EPALES
3
00400
PH
su
8.10
7.70
7.80
8.00
7.70
7.70
7.80
7.70
7.20
8.80
8.20
00410
T ALK
CAC03
MG/L
56
65
60
56
65
61
84
84
80
86
113
2111202
0014
00610
NH3-N
TOTAL
MG/L
0.030
0.050
0.090
0.040
0.060
0.090
0.140
0.130
0.220
U.420
0.280
FEET DEPTH
00625
TOT KJEL
N
MG/L
0.800
0.600
0.600
0.600
0.500
0.500
0.800
1.000
0.900
1.100
2.300
00630
N02&N03
N-TOTAL
MG/L
0.610
0.620
0.820
0.590
0.820
0.830
0.200
0.190
0.190
0.140
0.280
00671
PMOS-DIS
ORTHO
MG/L P
0.003
0.009
0.008
0.005
0.010
0.010
0.009
0.008
0.005
0.007
0.010
-------
STORET RETRIEVAL OATt 75/01/27
392906
. 40 59 00.0 081 05 41.0
bEHLlN RESERVOIR
39151 OHIO
11EPALES 2111202
3 0010 FEET
DATE
FROM
TO
73/04/24
73/07/30
DATE
FROM
TO
73/04/24
73/07/30
TIME DEPTH
OF
DAY FEET
14 35 0000
14 35 0005
14 35 0008
14 45 0000
14 45 OOOS
14 45 0008
10 55 0000
10 55 U005
10 55 0010
TIME DEPTH
OF
DAY FEET
14 35 0000
14 35 0005
14 35 0008
14 45 0000
14 45 0005
14 45 0008
10 55 0000
10 55 0005
10 S5 0010
00010
WATEU
TEMP
CENT
16.5
16.1
15.3
24. S
24.1
24.0
00665
PrIOS-TOT
MG/L P
0.121
0.110
U.117
0.097
0.101
C.121
0.036
0.161
0.221
00300
00
MG/L
9.0
8.0
5.6
3.6
32217
CHLRPMYL
A
UG/L
17.0
14.9
15.7
00077 00094
TRANSP CNDUCTVY
SECCHI FIELD
INCHES MiCROMHO
24 400
400
400
24 400
400
400
20 520
519
534
00400 00410
PH T ALK
CAC03
SU MG/L
7.90 74
7.70 74
7.70 74
7.80 73
7.80 74
7.70 74
9.30 95
7.70 118
7.40 120
00610
NH3-N
TOTAL
MG/L
0.110
0.100
0.160
0.110
0.110
0.150
0.100
0.270
U.600
DEPTH
00625
TOT
N
KJEL
MG/L
1
0
0
1
0
0
0
1
1
.000
.900
.700
.200
.900
.800
.800
.300
.600
00630
N02&N03
N-TOTAL
MG/L
0.930
0.920
0.930
0.930
0.920
0.930
0.290
0.650
0.890
00671
PHOS-DIS
OR TrlO
MG/L
0.
0.
0.
0.
0.
0.
0.
0.
0.
P
049
045
050
047
045
047
002
022
034
-------
STOKET HETR1EVAL DATE 75/01/27
392907
40 SB 23.0 081 06
btKLIN RESERVOIR
39151 OHIO
17.0
DATE TIME DEPTH
FROM OF
TO DAY FEET
73/04/24 15 00 0000
15 00 0005
15 10 0000
15 10 0005
00010
WATEK
TEMP
CENT
17.2
16.0
00300 00077 00094
DO TKANSP CNDOCTVY
SECCHI FIELD
MG/L INCHES M1CKOMHO
6.4
30
30
405
440
440
HEPALES
3
00400
PH
su
7.60
7.10
7.50
7,20
00410
T ALK
CAC03
MG/L
77
82
76
81
2111202
0008
00610
NH3-N
TOTAL
MG/L
0.120
U.220
0.140
0.220
FEET DEPTH
00625
TOT KJEL
N
MG/L
1.000
0.900
1.000
1.000
00630
N02&N03
N-TOTAL
MG/L
0.860
0.880
0.870
0.870
00671
PHOS-DIS
ORTHO
MG/L P
0.060
0.070
0.058
0.065
00665 32H17
DATE TIME DEPTH PHOS-TOT CHLRPHYL
FKOM OK A
TO OAY FEET MG/L P UG/L
73/04/24 15 00 UOOO u.238 22.0
15 00 0005 0.152
15 10 0000 0.136 21.6
15 10 OOOS 0.181
-------
APPENDIX E
TRIBUTARY and WASTEWATER
TREATMENT PLANT DATA
-------
RETRIEVAL DATE 7b/02/03
41 03 31.0 080 59 12.0
MAriONlNG KIVE*
7.b LH MILTON
KESEKV01R
HD tJKDG AT bhiLLINoS MILL
11EP«LLS 2111204
ft OOOU PEET UEHTH
OAlL
FROM
TO
7J/05/05
73/06/lU
73/07/22
73/06/18
73/09/29
73/10/20
73/11/0*
7J/12/02
7^/01/06
74/02/03
7^/02/lS
74/03/03
74/03/ib
74/0^/07
C0b3u 006£5
TIME DEPTH N02(iN03 TOT KJEL
OF N- TOTAL N
DAY FEET
13
09
10
09
10
11
10
10
14
13
12
11
11
11
55
45
15
10
00
10
30
30
00
55
00
10
40
05
MG/L
0
0
0
0
0
0
0
0
1
1
1
1
1
1
.860
.890
.280
.810
.340
.336
.420
.b20
.180
.bio
.520
.6Ut)
,4tG
.20u
MG/L
2.
1.
2.
1.
1.
1.
0.
0.
0.
1.
0.
1.
0.
0.
200
100
730
760
050
200
t.00
500
800
000
900
000
900
700
00610 00671 OUfab5
IMH3-N PnOS-OIS PhOS-TUT
TOTAL UHTHO
MG/L
0.
0.
u.
0.
0.
u.
0.
0.
0*
0.
0.
0.
0.
c.
066
245
720
480
2UU
050
012
Ob2
200
220
220
120
095
100
MG/L
U.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
u.
0.
0.
p
U05K
005K
022
030
015
009
005K
020
032
040
040
020
020
020
MG/L P
0.045
0.025
U. lOJ
o.ios
0.1)55
U.045
O.U30
0.035
O.J70
0.070
0.080
0.087
0.065
U.020
K VALUE ivNOwN TO tit
Lf.bS THAN i'\oiCrtTEo
-------
STORE! RETRIEVAL DATE 75/02/03
3-J29A2
40 55 59.0 081 Ob 44.0
HAHONING RIVER
39 7.b ALLIANCE
I/BERLIN KESERYOIR
wtbB RU bKOG N EOGE OF ALLIANCE
11LHALE5 2111204
4 0000 FEET DEPTH
DATE
FROM
TO
73/05/05
73/Ob/03
73/07/22
73/Od/18
73/0^/29
73/1J/2U
73/11/0**
73/12/02
7<*/01/06
74/02/03
74/02/15
74/03/03
74/03/16
74/04/07
00630 00625
TIME DEPTH N02&N03 TOT KJEL
OF N-TOTAL N
DAY FEET
15
11
11
10
11
12
11
12
Ib
14
13
12
13
10
35
30
30
4b
10
25
50
15
20
50
45
2b
10
05
MG/L
0.
0.
3.
0*
u.
0.
1.
1.
1.
1.
1.
2.
1.
1.
HBO
780
9uO
710
530
430
2t>y
900
760
760
400
000
430
060
MG/L
1
1
2
1
1
1
1
1
0
0
0
0
1
0
.100
.600
.600
.500
.POO
.200
.100
.600
.600
.600
.900
.700
.900
.BOO
00610 00671 00665
NH3-N PHOS-OIS PHO^-TOT
TOTAL ORTHO
MG/L
0.
0.
0.
0.
0.
0.
0.
0.
u.
0.
0.
0.
0.
0.
084
100
240
210
154
054
OOU
14H
168
115
is*o
065
165
05b
MG/L
0.
u.
0*
0.
0.
0.
0.
0.
0.
u.
0.
0.
0.
0.
p
052
049
078
086
13B
210
060
060
048
050
090
03b
075
025
MG/L P
0.100
0.135
U.240
J.23u
0.330
0.300
0.125
0.125
U.123
0.135
u.170
0.160
0.350
0.065
-------
STUKtT KETRIEVAL DATE 75/02/03
<*! 00 00.0 080 56 10.0
MILL CP.EEK
39 /.S DAMASCUS
T/oLKLlN h^ESErtVOlK
LEFFINGWtLL KJ HKOCj 1
lltPALES
<*
MI E UP CHWIbTlfTUW
2111204
0000 FEET DEPTH
DATE
FROM
TO
73/05/05
73/06/03
73/07/32
7j/t>a/l8
73/04/29
73/10/2U
73/11/04
7j/12/0>?
7<+/l>l/06
74/U2/03
74/02/15
74/03/03
7*/03/l6
74/04/07
00630 00625
TIME DEPTH N02S.N03 TOf KJEL
OF rg-TOTAL N
DAf FEET
16
11
12
11
11
12
12
12
15
15
14
ia
13
09
20
S5
02
10
45
50
10
45
*S
IS
10
55
35
40
MG/L
0.
0.
5.
0.
u.
u.
1.
2.
1.
1.
0.
2.
1.
0.
24U
069
500
660
072
013
040
000
500
260
910
64U
400
2H8
MG/L
1.
4.
2.
1.
1.
1.
1.
0.
0.
0.
0.
0.
1.
0.
260
500
450
7ftO
ISO
100
200
7QO
HOO
700
HOO
800
300
800
00610 00671 00665
NH3-N PHGS-Dlb PhOi-FOT
TOTAL URTriO
MG/L
0.
0.
u.
0.
0.
0.
0.
0.
0.
0.
u.
0.
0.
0.
031
014
139
097
056
03b
026
032
056
035
065
037
105
040
MG/L
0.
0.
0.
0.
0.
0.
0*
0.
i>.
0.
0.
0.
0.
0.
p
008
006
039
035
014
022
020
024
OOd
015
015
010
045
010
MG/L P
0.02b
0.050
0.110
O.OdO
0.070
0.022
U.04U
0.040
0.025
0.015
0.035
0.07^
0.1 70
0.035
-------
KETRIEVAL DATE 7b/02/03
3929C1
40 3d 22.U Odl 00 4b.U
INLAND CKEt'K
J9 7.5 ALLIANCE
T/BEKLIN KESEKV'OIK
2NORY HD dMDG 0.7 *I S OF NORTH bENTON
11EPALES 2111204
4 0000 FEET DEPTH
DATE
FROM
TO
73/06/05
73/06/03
73/07/22
73/08/18
73/09/29
73/10/20
73/11/04
73/12/02
74/01/06
74/02/15
7«+/03/03
74/03/16
74/04/07
00630 00625
TIME DEPTH NU2NN03 TOT KJEL
OF N- TOTAL N
DAY FEET
16
11
11
10
11
12
12
12
15
14
12
1J
09
05
45
45
55
30
45
00
30
HO
00
45
25
50
M(i/L
0
1
7
1
0
0
1
1
1
0
2
1
a
.470
,8oO
.700
.860
.410
.025
.920
.760
.3UO
.820
.200
.040
.312
MG/L
1.540
1.300
3.600
2.100
3.990
1.450
1.450
0.750
0.500
1.700
1.000
2.300
1.300
00610 00671 00665
NH3-N PriOS-DlS r'HOb-TOT
TOTAL OtfTHO
MG/L
0.
0.
0.
0.
1.
0.
0.
0.
0.
0.
0.
0.
0.
042
034
230
100
100
126
044
072
100
320
050
145
075
MG/L
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
G.
0*
P
033
012
075
IbO
028
060
100
040
02d
100
02B
OHO
025
MG/L f
0
0
0
0
G
0
0
0
0
0
0
0
0
.075
.lib
.155
.290
.300
.145
.Id5
.076
.035
.380
.110
.270
.040
-------
STOKET *EThUEVAL DAFfc. 75/02/03
3929J1
40 56 03.0 081 Ob 20.0
tiEECH CrtttK
3* 7.5 LiHAVlLLE
T/BEKLIN KESEKV01K
AEHI AVE tSKLJG .b Ml b OF ST *
llEPALEb 2111204
H 0000 FEET
DATE
FHOM
TO
73/05/05
73/06/03
73/07/2?
73/08/18
73/09/29
73/10/20
73/11/04
73/12/02
74/ul/Ob
74/02/03
74/02/ 15
74/03/03
74/03/16
74/04/07
00630 00625
TIME DEPTH N02&N03 TOT KJEL
OF h4-fOTAL N
DAY FEET
15
10
11
10
10
12
11
11
15
14
13
12
12
10
20
45
07
30
50
15
40
30
15
20
05
15
40
15
MG/L
0
i
6
0
0
0
1
1
1
1
1
2
1
0
.690
• 060
.100
.370
.310
.170
.800
.800
.760
.700
.400
.300
.400
.880
MG/L
1.
1.
3.
0.
1.
1.
1.
0.
0.
0.
0.
0.
1.
1.
260
100
ISO
780
470
200
250
700
500
500
800
900
700
100
00610
NM3-N F
TOTAL
MG/L
0
0
0
0
0
0
0
0
0
0
0
0
0
0
.028
.039
.126
.029
.147
.038
.048
.060
.115
.075
.145
.055
.215
.035
00671 00665
^HOs-OiS PHOS-rOT
OhiTHO
MG/L P
0
J
0
0
0
0
0
0
0
0
0
0
0
0
.042
.017
.060
.046
.105
.060
.052
.048
.036
.030
.035
.030
.080
.027
MG/L t>
U.075
0.050
0.165
0.080
0.430
0.070
0.095
0.085
0.070
0*060
0.080
U. 150
0.1 50
0.040
(JEPTH
-------
bTORET P.ETKIEVAL DATE 75/02/03
40 5b 10. 0 061 07 15.0
DEEP CHEEK KES 5PILLWAY
39 7.5 ALLIANCE
T/HEKL1N KESEHVOIR
DEEP CREEK RESEKVOIW
HEHALES 21H20A
^ 0000 FEET
DEPTH
DATE
FROM
TO
73/Ui/05
73/06/03
73/Od/lB
74/0^/15
7*4/03/03
74/03/16
74/04/07
TIME DEPTH
OF
UAY FEET
15 00
10 25
10 10
12 45
12 00
12 20
10 35
00630
N02MM03
N-TOTAL
MG/L
0.500
0.420
0.160
0.940
0.890
0.720
0.870
00625
TOT KJEL
N
MG/L
1.760
1.760
1.000
0.800
0.800
1.100
0.700
00610
NH3-N
TOTAL
MG/L
0.074
0.006
0.105
0.015
O.OSb
0.075
0.055
00671
PHOS-LJIS
OUTHO
MG/L P
0.006
O.OObK
0.016
0.007
O.OOSK
0.010
0.010
00665
PHOb-TJT
MG/L P
0.040
0.035
0.040
0.055
0.060
0.055
0.010
K VALUE ^NOWW TO HE
THAN INOICATEU
-------
bTORET KE.TR1EVAL DATE 75/02/03
41 01 30.U 031 04 47.0
WILLOW CRtEK
J9 /.b OEtKFltLU
1/btRLIH KtbEKVOiH
IMOTMAN HO BHOG N Of- US 224
11EPALES 2111204
4 UOUO FEET
DEPTH
DATE
FROM
TO
7J/05/05
73/1)6/03
73/07/2?
73/C3/1H
73/0^/29
73/10/20
73/11/04
73/12/02
74/U1/06
74/02/03
74/u2/lb
74/03/03
7^/03/lfa
74/ot/U7
J0630 00625
TIMt DEPTH ^02&N03 TOT KJEL
OF N-FOTAL N
DAY FEET
1<»
10
10
09
10
11
11
10
14
14
12
11
12
10
20
10
30
SO
20
45
10
46
30
10
30
?5
10
50
M(i/L
0.
0.
3.
0.
0.
0.
0.
0.
Cl.
0.
0.
1.
0.
0.
100
015
50C>
190
Od2
Oil
520
360
420
240
336
010
430
072
MG/L
1
1
2
0
1
0
1
0
0
0
0
0
0
0
.430
.OSO
• BOO
.BOO
.470
.600
.200
.bOO
.700
.300
.800
.800
.800
.400
00610 00671 U06t>6
NH3-N PnOb-DIS PHOS-TOf
TOTAL URTHQ
MG/L
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
048
010
231
046
077
046
044
OJ6
100
065
1S5
03b
060
045
MG/L
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
p
005K
007
015
008
OOBK
007
012
016
008
005K
006K
OOSK
010
005K
MG/L P
0.030
0.050
O.t>65
0.025
0.035
0.045
O.OnS
0.030
0.015
O.OOSK
0.08b
O.Obb
0.100
0.025
FHHN INDICATED
K VALUE MMOrtN TO «£
-------
RETRIEVAL DATE 7b/02/03
392VAA TF3929AA P030000*
40 5f 20.0 U81 07 1)5.0
ALLIANCE
39019 7.5 ALLIANCE
DEPTH
DATE
FROM
TO
73/Ob/14
CP(T>-
73/Oti/ 1*»
73/09/1^
73/10/14
73/11/14
73/12/14
74/01/14
7W02/14
CP(T)-
74/02/ 14
74/J3/14
CP(T)-
74/03/ 1**
7^/04/14
74/U5/ 14
74/06/ 14
CP(f >-
74/u6/ 15
74/U7/20
CP(T>-
74/07/21
74/08/13
CP-
7**/OH/ 14
CO 630
TIME DEPTH N02&N03
OF N- TOTAL
DAY FEET MG/L
00
24
07
07
06
OU
U2
00
24
06
06
06
06
Ob
06
00
OU
30
30
00
00
00
00
00
00
00
00
00
00
00
0
1
4
4
H
2
b
0
5
2
0
U
0
.040
.920
.900
.400
.4^0
.000
.100
.0-+0
.100
.ObO
.120
.080
.it aii
00625
Tor KJEL
N
MG/L
15.00U
14. ^00
9.800
21.000
11. bOO
17.000
10.000
11.000
5.400
9.3SO
18.000
15.000
19.000
00610 00671
NH3-N PHOS-DIS
TOTAL ORTHO
Mb/L MG/L P
0.740
2.220
0.220
4.800
0.052
3.680
1.400
O.ObO
0.210
4.000
V.600
3.700
4.300
7.240
5.200
6.100
3.590
S.tiuO
4.000
3.700
3.600
a. sco
6.200
4.800
T/bEKLiN RESERVOIR
MAHONlNli RIVER
HEPALtS 2141204
4 0000 FEET
Ou665 50051 b0053
PHOS-TOT FLU* CONDUIT
RATE FLJx-MGD
MG/L P INST MGD MONTHLY
10
6
5
7
5
8
5
b
s
5
V
7
b
.500
.45o
.600
.700
.500
.500
.000
.300
.000
.500
.100
.900
.400
2.4CO
2.400
2.500
2.640
3.400
J.400
2.700
3.400
3.*00
3.000
2.200
2.500
3. ICO
2.600
3.000
^.aoo
2.900
3.300
3.400
3.900
3.500
3.200
3.5UO
2.700
2.900
------- |