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

-------
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


-------