U.S. ENVIRONMENTAL PROTECTION AGENCY
           NATIONAL EUTROPHICATION SURVEY
                    WORKING PAPER SERIES
                                          REPORT
                                            ON
                                      GEIST RESERVOIR
                                  HAMILTON AND MARION COUNTIES
                                          INDIANA
                                        EPA REGION V
                                    WORKING PAPER No, 327
 CORVALLIS ENVIRONMENTAL RESEARCH LABORATORY - CORVALLIS, OREGON
                             and
ENVIRONMENTAL MONITORING & SUPPORT LABORATORY - LAS VEGAS, NEVADA
 699-440

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                                                        REPORT
                                                          ON
                                                   GEIST RESERVOIR
                                             HAMILTON AND WRION COOTIES
                                                       INDIANA
^                                                    EPA REGION V
en
                                                WORKING PAPER No, 327
                            WITH THE COOPERATION OF THE
                            INDIANA STATE BOARD OF HEALTH
                                     AND THE
                              INDIANA NATIONAL GUARD
                                   APRIL, 1976

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                                   CONTENTS
                                                               Page
  Foreword                                                      ii
  List of Indiana Study Lakes                                   iv
  Lake and Drainage Area Map                                     v

  Sections
  I.   Conclusions                                                1
 II.   Lake and Drainage Basin Characteristics                    4
III.   Lake Water Quality Sunmary                                 5
 IV.   Nutrient Loadings                                          9
  V.   Literature Reviewed                                       16
 VI.   Appendices                                                17

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                                 n
                          FOREWORD
    The National Eutrophication Survey was initiated in 1972 in
response to an Administration commitment to investigate the nation-
wide threat of accelerated eutrophication to fresh water lakes and
reservoirs.

OBJECTIVES

    The Survey was designed to develop, in conjunction with state
environmental agencies, information on nutrient sources, concentrations,
and impact on selected freshwater lakes as a basis for formulating
comprehensive and coordinated national, regional, and state management
practices relating to point-source discharge reduction and non-point
source pollution abatement in lake watersheds.

ANALYTIC APPROACH

    The mathematical and statistical procedures selected for the
Survey's eutrophication analysis are based on related concepts that:

        a.  A generalized representation or model relating
    sources, concentrations, and impacts can be constructed.

        b.  By applying measurements of relevant parameters
    associated with lake degradation, the generalized model
    can be transformed into an operational representation of
    a lake, its drainage basin, and related nutrients.

        c.  With such a transformation, an assessment of the
    potential for eutrophication control can be made.

LAKE ANALYSIS

    In this report, the first stage of evaluation of lake and water-
shed data collected from the study lake and its drainage basin is
documented.  The report is formatted to provide state environmental
agencies with specific information for basin planning {§303(e)K water
quality criteria/standards review {§303(c)>, clean lakes (§314(a,b)},
and water quality monitoring {§106 and §305(b)} activities mandated
by the Federal Water Pollution Control Act Amendments of 1972.

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    Beyond the single lake analysis, broader based correlations
between nutrient concentrations (and loading) and trophic condi-
tion are being made to advance the rationale and data base for
refinement of nutrient water quality criteria for the Nation's
fresh water lakes.  Likewise, multivariate evaluations for the
relationships between land use, nutrient export, and trophic
condition, by lake class or use, are being developed to assist
in the formulation of planning guidelines and policies by EPA
and to augment plans implementation by the states.

ACKNOWLEDGMENT

    The staff of the National Eutrophication Survey (Office of
Research & Development, II. S. Environmental Protection Agency)
expresses sincere appreciation to the Indiana State Board of
Health for professional involvement, to the Indiana National
Guard for conducting the tributary sampling phase of the Survey,
and to those Indiana wastewater treatment plant operators who
provided effluent samples and flow data.

    The staff of the Division of Water Pollution Control, Indiana
State Board of Health, provided invaluable lake documentation and
counsel during the Survey, reviewed the preliminary reports, and
provided critiques most useful in the preparation of this Working
Paper series.

    Major General Alfred F. Ahner, Adjutant General of Indiana,
and Project Officers Lt. Colonel Charles B. Roberts (Retired)
and Colonel Robert L. Sharp, who directed the volunteer efforts
of the Indiana National Guardsmen, are also gratefully acknowledged
for their assistance to the Survey.

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                                    iv
                      NATIONAL EUTROPHICATION SURVEY

                               STUDY LAKES

                             STATE OF INDIANA
LAKE NAME

Bass
Cataract
Crooked
Dallas
Geist
Hamilton
Hovey
James
James
Long
Marsh
Mississinewa
Maxinkuckee
Monroe
Morse
01 in
Oliver
Pigeon
Syl van
Ti ppecanoe
Versailles
Wawassee
Webster
Westler
Whitewater
Winona
Wi trier
COUNTY

Starke
Owen, Putnam
Steuben
LaGrange
Hamilton, Marion
Steuben
Posey
Kosciusko
Steuben
Steuben
Steuben
Grant, Miami, Wabash
Marshall
Brown, Monroe
Hami1 ton
LaGrange
LaGrange
Steuben
Noble
Kosciusko
Ripley
Kosciusko
Kosciusko
LaGrange
Union
Kosciusko
LaGrange

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  - 40-00'
                 Map Location

                    (indT
*\
  Fall
  Creek
GEIST    RESERVOIR

(g) Tributary Sampling  Site
 X Lake Sampling Site
 P Sewage Treatment  Facility
^•Drainage Area Boundary
9          _J	IP Km.
                                                                                      s Mi.
                                                                             Scale
	39°50'
                               85' 50
                                                                85° 40'
                                                                                                 85'30

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                             GEIST RESERVOIR
                             STORE! NO.  1811

I.  CONCLUSIONS
    A.  Trophic Condition:
            Survey data indicate that Geist Reservoir is  eutrophic.   It
        ranked 17th when the 27 Indiana  lakes sampled in  1973 were compared
        using a combination of six parameters*.   Nineteen of the lakes
        had less median total phosphorus, nine had less median dissolved
        phosphorus, 17 had less median inorganic nitrogen, 23 had less
        mean chlorophyll a_, and 22 had greater mean Secchi disc trans-
        parency.
            Survey limnologists noted emergent and submerged aquatic macro-
        phytes at sampling station 2 and emergent macrophytes along parts
        of the shoreline.
    B.  Rate-Limiting Nutrient:
            The algal assay results indicate that Geist Reservoir was
        limited by phosphorus at the time the sample was  taken (05/10/73).
        The reservoir data indicate phosphorus limitation at all sampling
        times.
    C.  Nutrient Controllability:
            1.  Point sources—During the Survey sampling year, five point
        sources provided samples.   In May of 1975, the Indiana Division of
        Water Pollution Control identified six additional point sources in
* See Appendix A.

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                             2
the Fall River drainage, determined the phosphorus contribution
of four of them, and provided the data for this report (Bon-
Honrne, 1976).  The inclusion of the additional point-source loads
permits a more realistic assessment of phosphorus controllability.
    It is calculated that the phosphorus contribution of point
sources accounted for 32.5% of the total load to Geist Reservoir.
The Fortville wastewater treatment plant contributed 10.9%, the
Indiana State Reformatory plant contributed 7.6%, and the Middletown
plant contributed 6.1% of the total.  The remaining six measured
point sources collectively contributed 8.0% of the total phosphorus
load.   The loads from an elementary school and a church camp  were
not determined but probably were relatively insignificant compared
to the measured sources.
    The reservoir loading of 2.87 g/m2/yr is three times that pro-
posed by Vollenweider (Vollenweider and Dillon, 1974) as a eutro-
phic loading (see page 15).  However, the mean hydraulic retention
time of the reservoir is a relatively short 58 days, and Vollen-
weider 's model may not apply.
    While even complete removal of phosphorus at the listed point
sources would still leave a loading of 1.9 g/m2/yr (ca. twice the
eutrophic loading), in view of the questionable applicability of
Vollenweider's model and the phosphorus-limited condition of the
reservoir, it is likely that a high degree of phosphorus removal
at the significant point sources would result in improvement  in

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                             3
the trophic condition of the reservoir.
    2.  Non-point sources—The phosphorus contributions of non-
point sources accounted for 67.2% of the total  input to the
reservoir.  Fall Creek contributed 48.6%, and the remaining
three sampled tributaries collectively contributed 12.5% of the
total load.  The ungaged tributaries were estimated to have con-
tributed 5.5% of the total.
    The phosphorus export rate of Dry Branch was a rather high
57 kg/km2/yr.  The higher rate may be due in part to the un-
measured McCordsville Elementary School septic-tank load and in
part to septic tank drainage from the community of McCordsville.

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                                      4
II.   LAKE AND DRAINAGE BASIN CHARACTERISTICS1"
     A.   Lake Morphometry  :
         1.   Surface area:   7.28 kilometers2.
         2.   Mean depth:   3.6 meters.
         3.   Maximum depth:   6.7 meters.
         4.   Volume:  26.208 x 106  m3.
         5.   Mean hydraulic  retention  time:  58  days.
     B.   Tributary and Outlet:
         (See Appendix C  for flow data)
         1.   Tributaries  -
                                              Drainage       Mean flow
             Name                             area  (km2)*    (m3/_sec)*
             Fall Creek                           440.8          4.21
             Dry Branch                             19.7          0.18
             Flatfork Creek                          26.9          0.25
             Thorpe Creek                           24.6          0.23
             Minor tributaries  &
              immediate drainage -                   39 .j          0.35
                              Totals               551.9          5.22
         2.   Outlet -
             Fall Creek                           559.2**        5.22**
     C.   Precipitation***:
         1.   Year of sampling:   122.0  centimeters.
         2.   Mean annual: 100.8 centimeters.
 t  Table of metric conversions—Appendix  B.
 tt Winters,  1975.
 *  For limits of accuracy,  see Working  Paper  No.  175,  "...Survey Methods,
   1973-1976".
 ** Includes area of lake;  outflow adjusted to  equal sum of inflows.
 *** See Working Paper No.  175.

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                                       5
III.   LAKE WATER QUALITY SUMMARY
      Geist Reservoir was sampled three times  during  the open-water
  season of 1973 by means of a  pontoon-equipped  Huey  helicopter.   Each
  time, samples for physical  and chemical  parameters  were  collected
  from a number of depths at two stations  on the reservoir (see map,
  page v).  During each visit,  a single depth-integrated (4.6 m or
  near bottom to surface) sample was  composited  from  the stations  for
  phytoplankton identification  and enumeration;  and during the first
  visit, a single 18.9-liter depth-integrated  sample  was composited
  for algal assays.  Also each  time,  a  depth-integrated sample was
  collected from each of the stations for  chlorophyll  a_ analysis.  The
  maximum depths sampled were 4.3 meters at station 1  and  6.1 meters
  at station 2.
      The sampling results are  presented in full  in Appendix D and
  are summarized in the following table.

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PARAMETER

TEMP (C)

DISS OXY 1MG/L)

CNDCTVY (MCROMO)

PH (STAND UNITS)

TOT ALK (MG/L)

TOT P (MG/L)

ORTHO P (MG/L)

N02«N03 (MG/L)

AMMONIA (MG/L)

KJEL N  (MG/L)

INORG N (MG/L)

TOTAL N (MG/L)

CHLHPYL A (UG/L)

SECCHI  (METERS)
                             A. SUMMARY OF PHYSICAL AND


                             1ST SAMPLING ( 5/10/73)

                                   2 SITES
CHEMICAL CHARACTERISTICS FOR
 STORET CODE 1811
                                                                                      GEIST  RESERVOIR
           2ND SAMPLING ( 8/ 2/73)

                 2 SITES
3RD SAMPLING 110/15/73)

      2 SITES
RANGE
16.2
7.8
530.
8.1
196.
0.050
0.004
2.210
0.060
0.600
2.280
2.920
34.9
O.S
- 18.2
- 11.2
- 590.
8.4
- 260.
- 0.089
- 0.013
- 3.020
- 0.150
- 0.800
- 3.140
- 3.690
- 54.2
0.9
MEAN
17.3
9.5
560.
8.3
223.
0.063
0.007
2.641
0.079
0.700
3.720
3.341
44.5
0.7
MEDIAN
17.3
9.6
560.
8.3
198.
0.058
0.006
2.890
0.060
0.700
2.950
3.590
44.5
0.7
RANGE
25.3
3.4
442.
7.7
159.
0.043
0.009
0.330
0.030
1.100
0.360
2.090
17.4
0.4
- 26.3
- 10.8
- 491.
8.6
- 185.
- 0.179
- 0.027
- 0.990
- 0.330
- 2.200
- 1.320
- 2.530
- 94.1
1.0
MEAN
25.9
7.7
46f.
8.4
170.
0.097
0.014
0.740
0.128
1.520
0.868
2.260
55.7
0.7
MEDIAN
26.0
8.8
453.
8.5
163.
0.059
0.010
0.990
0.090
1.200
1.080
2.190
55.7
0.7
RANGE
19.6
6.8 .
391.
8.3
151.
0.074
0.006
0.060
0.070
0.900
0.150
0.970
4.7
0.6
- 20.8
7.8
- 458.
8.4
- 190.
- 0.137
- 0.016
- 0.120
- 0.120
- 1.200
- 0.210
- 1.320
- 70.4
0.8
MEAN
20.3
7.2
418.
8.3
166.
0.098
0.011
0.079
0.104
1.057
0.183
1.136
37.5
0.7
MEDIAN
20.6
7.0
394.
8.3
155.
0.092
0.009
0.080
0.110
1.000
0.180
1.080
37.5
0.7

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B.  Biological  characteristics:

    1.   Phytoplankton -
        Sampling
        Date

        05/10/73
        08/02/73
        10/15/73
    2.   Chlorophyll  a_ -

        Sampling
        Date

        05/10/73
        08/02/73


        10/15/73
Dominant
Genera
1.
2.
3.
4.
5.
1.
2.
3.
4.
5.
1.
2.
3.
4.
5.
Melosira sp.
Cyclotella sp.
Dactylococcopsis sp,
Asterionella sp.
Stepjianodiscus sp.
Other genera
Total
Centric diatoms
Flagellates
Melosira S£.
Eucjlena sp.
Synedra sp.
Other genera
Total
Centric diatoms
Melosira sp.
Flagellates
Oscillatoria sp.
Merismopedia sp.
Other genera
                                             Total
Station
Number

   1
   2

   1
   2

   1
   2
                           Algal  Units
                           per ml

                             1,803
                             1,277
                               992
                               947
                               841
                             5,438
                            11,298

                            11,605
                             9,579
                             6,868
                               468
                               426
                             2.884

                            31,830

                            14,908
                             4,820
                             3,479
                             2,335
                             1,888
                             8.251

                            35,681
Chlorophyll
(yg/D

    54.2
    34.9

    94.1
    17.4

    70.4
     4.7

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                                 8
C.  Limiting Nutrient Study:
    1.  Autoclaved, filtered, and nutrient spiked -
                         Ortho P          Inorganic  N    Maximum yield
        Spike (mq/1)     Cone, (mg/1)      Cone,  (mg/1)    (mg/1-dry wt.)
        Control              0.015             2.380            3.4
        0.050 P             0.065             2.380           20.6
        0.050P+1.0N     0.065             3.380           21.8
        1.0 N               0.015             3.380            2.9
    2.  Discussion -
            The control yield of the assay alga,  Selenastrum capri-
        cornutum, indicates that the potential  primary  productivity
      .  of Geist Reservoir was moderately high at the time the sample
        was taken (05/10/73).  Also, a six-fold increase in yield
        with the addition of only phosphorus indicates  the reservoir
        was phosphorus limited at that time.  Note that the addition
        of only nitrogen resulted in a yield not  significantly dif-
        ferent from that of the control.
            The reservoir data also indicate phosphorus limitation;
        i.e., the mean inorganic nitrogen to orthophosphorus ratios
        were 17 to 1 or greater at all sampling times,  'and phosphorus
        limitation would be expected.

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IV.   NUTRIENT LOADINGS
     (See Appendix E  for  data)
     For the determination  of nutrient loadings, the  Indiana National
 Guard collected monthly  near-surface grab samples from each of the
 tributary sites indicated  on the map (page v), except for the high
 runoff months of February  and  March when two samples were collected.
 Sampling was begun in  June,  1973, and was completed  in May, 1974.
     Through an interagency agreement, stream flow estimates for the
 year of sampling and a "normalized" or average year were provided by
 the Indiana District Office  of the U.S. Geological Survey for the
 tributary sites nearest  the  reservoir.
     Except for Flatfork  Creek,  nutrient loads for sampled tributaries
 were determined by using a modification of a U.S. Geological Survey
 computer program for calculating stream loadings*.  The phosphorus
 load measured in Flatfork  Creek at station C-l was less than the
 Fortville wastewater treatment plant load, and the non-point nutrient
 loads of this stream were  estimated (see below).  The Fall Creek
 nutrient loads shown are those measured minus the point-source loads.
     Nutrient loads for Flatfork Creek and unsampled  "minor tributaries
 and immediate drainage"  ("ZZ"  of U.S.G.S.) were estimated using the
 nutrient loads at station  D-l,  in kg/km2/year, and multiplying by the
 Flatfork Creek and ZZ  areas  in  km2.
 * See Working  Paper  No.  175.

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                                    10

    The operators of the Indiana State Reformatory,  Pendleton, Middle-

town, Fortville, and Shenandoah High School  wastewater treatment  plants

provided monthly effluent samples and corresponding  flow data.

    The estimated phosphorus load from septic tanks  was reduced by

50% to adjust for a phosphate detergent ban  which has  been  in effect

in Indiana since January, 1972.

    A.  Waste Sources:

        1.  Known domestic  -


        Name

        Indiana State
         Reformatory
        Pendleton
        Middletown
        Fortville
        Ingalls
        Regency MHP

        Shenandoah
         High Sch.*
        McCordsville
         El em. Sch.
        U. Pentecostal
         Camp
Pop.
Served
2,300
2,496
2,300
2,480
888
?

700
?

?

Treatment
tr. filter
act. sludge
tr. filter
tr. filter
septic tanks
ext. aer.
+ pond
act. sludge
septic tank

ext. aer.
Mean Flow
(mVd)
1,403.3
881.4
1,539.5
1,860.8
336.1
11.4

11.4
?

113.6**
Receiving
Water
Fall Creek
Fall Creek
Fall Creek
Flatfork Creek
Lick Creek
Fall Creek

Deer Creek
Stansbury Ditch/
Dry Branch
Lick Creek
t Treatment plant questionnaires; Anonymous, 1971.
* School operates 9 mo./year; pop. equivalent=125.
** Design flow.

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                                  11
      2.  Known industrial* -
      Name

      E. I. DuPont
       Nemours Co.

      Brookside Corp.
       #1
       #2
      Forthrite Div.,
       Richardson Co.
        #1

        #2
Treatment

neutralization
metal recovery
lagoon
(washwater)

septic tank
Mean Flow
(m'/d)

     26.5
     75.7
    128.7
     50.7

no discharge
Receiving
Water

Stottlemeyer
 Ditch/Flat-
 fork Creek

Dry Branch Creek
Dry Branch Creek
Stansbury Ditch/
 Dry Branch
Stansbury Ditch/
 Dry Branch
BonHomme, 1976.

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                                    12

    B.  Annual Total Phosphorus Loading - Average  Year:

        1.  Inputs -

                                              kg P/           % of
            Source                            yr              total
            a.  Tributaries (non-point load)  -

                Fall Creek                    10,175           48.6
                Dry Branch                     1,130            5.4
                Flatfork Creek                   780            3.7
                Thorpe Creek                     710            3.4

            b.  Minor tributaries & immediate
                 drainage (non-point load)  -    1,155            5.5

            c.  Known domestic STP's -

                Indiana State Reformatory      1,600            7.6
                Pendleton                        930            4.4
                Middletown                     1,270            6.1
                Fortville                      2,275           10.9
                Regency MHP                      110            0.5
                Shenandoah High School            10           <0.1
                McCordsville El em. Sch.          ?
                Pentecostal Camp                 ?

            d.  Septic tanks* -                   55            0.3

            e.  Known industrial -

                E. I. DuPont Nemours              60            0.3
                Brookside Corp.                  540            2.6
                Forthrite Div.                    20           <0.1

            f.  Direct precipitation** -         125            0.6

                        Total                 20,945          100.0

        2.  Outputs -

            Lake outlet - Fall Creek          12,625

        3.  Net annual P accumulation - 8,320 kg.
* Estimate based on 1970 Census of Ingalls and 38 lakeshore dwellings;  see
  Working Paper No. 175.
** See Working Paper No. 175.

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                                    13

    C.  Annual Total Nitrogen Loading - Average Year:

        1.   Inputs -

                                              kg N/          % of
            Source                            yr             total

            a.  Tributaries (non-point load)  -

                Fall Creek                    444,795          66.8
                Dry Branch                     36,200           5.4
                Flatfork Creek                 45,435           6.8
                Thorpe Creek                   41,545           6.2

            b.  Minor tributaries & immediate
                 drainage (non-point load) -    67,390          10.1

            c.  Known domestic STP's -

                Indiana State Reformatory       2,850           0.4
                Pendleton                       3,750           0.6
                Middletown                      5,155           0.8
                Fortville                       6,390           1.0
                Regency MHP                       ?
                Shenandoah High School             20          <0.1
                McCordsville El em. Sch.           ?
                Pentecostal Camp                  ?

            d.  Septic tanks* -                 4,190           0.6

            e.  Known industrial -

                E. I. DuPont Nemours              ?
                Brookside Corp.                   ?
                Forthrite Div.                    ?

            f.  Direct precipitation** -        7.860           1.2

                        Total                 665,580         100.0

        2.   Outputs -

            Lake outlet - Fall Creek          681,175

        3.   Net annual N loss - 15,595 kg.
* Estimate based on 1970 Census of Ingalls and 38 lakeshore dwellings;  see
  Working Paper No. 175.
** See Working Paper No. 175.

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                                14

D.  Mean Annual  Non-point Nutrient Export by  Subdrainage Area:

    Tributary                             kg  P/km2/yr    kg N/km2/yr

  ,  Fall Creek                                23           1,009
    Dry Branch                                57           1,838
    Thorpe Creek                              29           1,689

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                                    15
    E.  Yearly Loads:
            In the following table, the existing phosphorus loadings
        are compared to those proposed by Vollenweider (Vollenweider
        and Dillon, 1974).   Essentially, his "dangerous" loading  is
        one at which the receiving water would become eutrophic or
        remain eutrophic; his "permissible" loading is that which
        would result in the receiving water remaining oligotrophic
        or becoming oligotrophic if morphometry permitted.   A meso-
        trophic loading would be considered one between "dangerous"
        and "permissible".
            Note that Vollenweider's model may not be applicable  to
        water bodies with short hydraulic retention times.
                                  Total Phosphorus       Total  Nitrogen
        	Total   Accumulated    Total    Accumulated
        grams/m2/yr             2.88       1.14        91.4       loss*

        Vollenweider phosphorus loadings
         (g/m2/yr) based on mean depth and mean
         hydraulic retention time of Geist Reservoir:
            "Dangerous"  (eutrophic loading)              0,92
            "Permissible"  (oligotrophic loading)          0.46
* There was an apparent nitrogen loss during the sampling year.   This  may
  have been due to nitrogen fixation in the reservoir,  solubilization  of
  previously sedimented nitrogen, recharge with nitrogen-rich ground water,
  or unknown point sources discharging directly to the  reservoir.   What-
  ever the cause,  a similar loss has occurred at Shagawa Lake, Minnesota,
  which has been intensively studied by EPA's former National  Eutrophication
  and Lake Restoration Branch (Malueg et al., 1975).

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                                    16

V.  LITERATURE REVIEWED

    Anonvmous, 1971.  Inventory of waste treatment facilities.   EPA  Publ.
        OWP-1, vol. 5, Wash., DC.

    BonHomme, Harold L., 1976.  Personal communication (review  of pre-
        liminary report; point-source data).   IN Div.  of Water  Poll.  Contr.,
        Indianapolis.

    Malueg, Kenneth W., D. Phillips Larsen, Donald W.  Schults,  and Howard
        T. Mercier; 1975.  A six-year water,  phosphorus, and nitrogen bud-
        get for Shagawa Lake, Minnesota.  Jour.  Environ. Qual., vol.  4,
        no. 2, pp. 236-242.

    Vollenweider, R. A., and P. J. Dillon, 1974.  The  application of
        the phosphorus loading concept to eutrophication research.
        Natl. Res. Council of Canada Publ. No. 13690,  Canada Centre
        for Inland Waters, Burlington, Ontario.

    Winters, John, 1975.  Personal communication (reservoir morphometry).
        IN Div. of Water Poll. Contr., Indianapolis.

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VI.  APPENDICES
                                  APPENDIX A
                                 LAKE RANKINGS

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LAKE DATA TO BE USED IN RANKINGS
LAKE
CODE
1805
1811
1817
1837
1828
1829
1836
1837
1839
1840
1841
1842
1843
1844
18*5
1846
1847
1848
1849
1850
1851
.852
1853
1854
1855
1856
1857
LAKE NAME
CATARACT LAKE
GEIST RESERVOIR
JAMES LAKE
MISS1SSINEKA RESERVOIR
MONKOE RESERVOIR
MORSE RESERVOIR
HAHASEE LAKE
WEBSTER LAKE
WHITEWATER LAKE
WINONA LAKE
WESTLER LAKE
WITMER LAKE
LAKE MAXINKUCKEE
TIPPECANOE LAKE
DALLAS LAKE
OLIN LAKE
OLIVER LAKE
SYLVAN LAKE
HOVEY LAKE
VERSAILLES LAKE
BASS LAKE
CROOKED LAKE
LAKE JAMES
LONG LAKE
PIGEON LAKE
MARSH LAKE
HAMILTON LAKE
MEDIAN
TOTAL P
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
.058
.074
.024
.107
.025
.084
.012
.025
.084
.035
.035
.035
.020
.019
.029
.012
.009
.170
.062
.139
.040
.019
.016
.204
.058
.093
.033
MEDIAN
INORG N
1.66Q
1.080
1.030
2.400
0.325
3.325
0.210
0.790
1.62C
1.250
0.860
0.900
0.220
0.195
0.830
1.460
0.920
0.130
1.050
1.090
0.250
0.120
0.190
1.920
1.945
0.270
0.720
500-
MEAN SEC
466
472
434
473
43b
473
364
431
470
444
427
440
400
391
413
403
392
469
489
482
471
410
352
442
442
451
413
.667
.500
.000
.444
.623
.222
.500
.000
.167
.667
.125
.333
.400
.500
.333
.333
.000
.833
.333
.000
.375
.111
.444
.667
.667
.333
.167
MEAN
CHLOHA
10
45
11
15
b
56
5
11
33
11
10
11
5
6
10
4
3
47
84
25
29
5
4
16
11
34
17
.744
.950
.533
.778
.947
.167
.000
.500
.083
.211
.712
.917
.483
.050
.067
.867
.767
.480
.267
.078
.367
.578
.856
.100
.900
.467
.450
15-
MIN DO
15
11
15
15
15
15
14
15
15
15
15
15
15
15
15
14
14
14
7
14
7
15
15
15
15
15
15
.000
.600
.000
.000
.000
.000
.600
.000
.000
.000
.000
.000
.000
.000
.000
.900
.800
.800
.600
.500
.000
.000
.000
.000
.000
.000
.000
MEDIAN
DISS OrtTriO f
0.01J
0.009
0.008
0.029
o.oor
0.009
0.003
0.005
0.012
0.011
0.013
0.011
0.003
0.005
0.014
0.003
0.004
0.017
0.024
0.019
0.012
0.005
0.005
0.150
0.015
0.055
0.018

-------
PERCENT OF  LAKES WITH HIGHER VALUES  (NUMBKK OF LAKES WITH HIGHEx  VALUES*
LAKE
CODE
1805
1811
1817
1827
1828
1H29
1836
1837
Ift39
1840
1841
1842
1843
1844
1845
1846
1847
1848
1849
1850
1851
1852
1853
1854
1855
1856
1857
LAKE NAME
CATARACT LAKE
GEIST RESERVOIR
JAMES LAKE
MISSISSINEWA RESERVOIR
MONROE RESERVOIR
MORSE RESERVOIR
WAWASEE LAKE
WEBSTER LAKE
WHITEWATER LAKE
WINONA LAKE
WESTLER LAKE
WITHER LAKE
LAKE MAXINKUCKEE
TIPPECANOE LAKE
DALLAS LAKE
OLIN LAKE
OLIVER LAKE
SYLVAN LAKE
HOVEY LAKE
VERSAILLES LAKE
BASS LAKE
CROOKED LAKE
LAKE JAMES
LONG LAKE
PIGEON LAKE
MARSH LAKE
HAMILTON LAKE
MEDIAN
TOTAL f
37
27
73
12
67
?3
94
67
19
50
50
50
77
85
62
94
100
4
31
8
42
81
88
0
37
15
58
I 9)
( 7)
( 191
( 31
( 17)
( 6)
( 24)
( 17)
( 5)
( 12)
( 12)
I 12)
I 20)
( 22)
( 16)
I 24)
( 26)
( D
( 6)
( 2)
( 11)
( 21)
I 23)
( 0)
( 9)
( 4)
( 15)
MEDIAN
INOWG N
15
35
42
4
b9
0
85
62
19
27
54
50
81
88
58
23
46
96
38
31
77
100
92
12
8
73
65
( 41
( 9)
( 11)
( 1)
I 18)
( 0)
< 22)
( 16)
( 5)
( 7)
( 14)
( 13)
( 21)
< 23)
( 15)
( 6)
< 12)
( 25)
( 10)
( 8)
( 201
( 26)
( 24)
( 3)
( 2)
( 19)
( 17)
500-
MEAN SEC
31
15
be
8
54
12
96
62
23
38
65
50
85
92
69
81
88
27
0
4
19
77
100
44
44
35
73
( 8)
( 4)
( 15)
( 2)
( 14)
( 3)
o
< 25)
( 16)
( 6)
( 10)
( 17)
( 13)
( 22)
( 24)
( 18)
( 21)
( 23)
( 7)
( 0)
( 1)
( 5)
I 20)
( 26)
( 11)
( 11)
( 9)
( 19)
MEAN
CHLORA
62
12
50
38
73
4
88
54
19
58
65
42
85
77
69
92
100
8
0
27
23
81
96
35
46
15
31
( 16)
I 3)
I 13)
( 10)
( 19)
( 1>
I 23)
( 14)
( 5)
( 15)
( 17)
( 11)
( 22)
( 20)
( 18)
( 24)
( 26)
( 2)
( 0)
( 7)
( 6)
I 21)
( 25)
I 9)
I 12)
I 4)
I H)
15-
MIN DO
35
92
35
35
35
35
85
35
35
35
35
35
35
35
35
73
79
79
96
88
100
35
35
35
35
35
35
( 0)
( 24)
( 0)
( 0)
( 0)
I 0)
< 221
( 0)
( 0)
( 0)
( 0)
( 0)
( 0)
( 0)
( 0)
I 19)
( 20)
( 20)
( 25)
( 23)
( 26)
I 0)
I 0)
( 0)
( 0)
I 0)
( 0)
MEDIAN
DISS ORTHO P
37
62
65
8
69
58
98
81
42
52
37
52
98
85
31
92
88
23
12
15
46
75
75
0
27
4
19
( 9)
I 16)
1 17)
( 2)
( 18)
( 15)
< 251
( 21)
I ID
( 13)
( 9)
( 13)
( 25)
( 22)
( B>
( 24)
< 23)
( 6)
I 31
( 4)
( 12)
( 19)
( 19)
( 0)
( 7)
( 1)
( 5)
INJEX
NO
217
243
323
105
367
132
546
361
157
260
306
279
461
462
324
455
501
237
177
173
307
449
486
126
141
177
231

-------
LAKES RANKED sr INDEX NOS.




RANK  LAKE CODE  LAKE NAME               INDEX NO






   1  1836       WAMASEE LAKE               546




   2  1847       OLIVER LAKE                501



   3  1853       LAKE JAMES                 486



   4  1844       TIPPECANOE LAKE            462



   5  1843       LAKE MAXINKUCKEE           461



   6  1846       OLIN LAKE                  455



   7  1852       CROOKED LAKE               449



   8  1828       MONROE RESERVOIR           367



   9  1837       WEBSTER LAKE               361



  10  1845       DALLAS LAKE                324



  11  1817       JAMES LAKE                 323



  12  1851       BASS LAKE                  307



  13  1841       WESTLER LAKE               306



  14  1857       HAMILTON LAKE              281



  15  1842       WITMER LAKE                279



  16  1840       WINONA LAKE                260



  17  1811       GEIST RESERVOIR            243



  18  1848       SYLVAN LAKE                237



  19  1805       CATARACT LAKE              217



  20  1855       PIGEON LAKE                197



  21  1856       MARSH LAKE                 177



  22  1849       HOVEY LAKE                 177



  23  1850       VERSAILLES LAKE            173



  24  1839       ilHITEHATER LAKE            157



  25  1629       MORSE RESERVOIR            132



  26  1854       LONG LAKE                  126



  27  1827       MISSISSINEKA RESERVOIR     105

-------
    APPENDIX B
CONVERSION FACTORS

-------
                CONVERSION FACTORS

Hectares x 2.471 = acres
Kilometers x 0.6214 = miles
Meters x 3.281 = feet
Cubic meters x 8.107 x 10   = acre/feet
Square kilometers x 0.3861 = square miles
Cubic meters/sec x 35.315 = cubic feet/sec
Centimeters x 0.3937 = inches
Kilograms x 2.205 = pounds
Kilograms/square kilometer x 5.711 = Ibs/square mile

-------
    APPENDIX C
TRIBUTARY FLOW DATA

-------
                                   TRIBUTARY FLOW INFORMATION FOR INDIANA
                                                                                          03/39/76
LAKE CODE Iftll     GEIST RESERVOIR

     TOTAL DRAINAGE AREA OF LAKE(SO KM)
          SUB-DRAINAGE
TRIBUTARY  AREA(SQ KM)
                          JAN
                                  FEB
                                           557.1
                                          MAR
                                                  APR
                                                          MAY
             NORMALIZED FLOWS(CMS)
               JUN     JUL     AUG
                                                                                          SEP
                                               OCT
                                                                                                          NOV
                                                                                                                  DEC
                                                                                                                         MEAN
leiiAi
1811A2
1811B1
1811C1
181101
1811ZZ
559.2
440.8
19.7
26.9
24.6
37.8
7.39
5.78
0.227
0.311
0.283
0.453
8.16
6.43
0.280
0.396
0.340
0.538
11.10
8.78
0.425
0.566
0.510
0.765
10.62
8.38
0.368
0.510
0.481
0.708
7.02
5.52
0.241
0.340
0.311
0.453
5.18
4.08
0.184
0.252
0.232
0.368
3.26
2.55
0.110
0.150
0.139
0.212
1.47
1.13
0.034
0.048
0.045
0.071
1.25
0.96
0.034
0.048
0.042
0.068
1.39
1.08
0.037
0.051
0.045
0.074
2.75
2.18
0.096
0.130
0.119
0.184
4.81
3.79
0.181
0.246
0.227
0.340
5.35
4.21
0.184
0.253
0.230
0.351
                                                                   SUMMARY
                        TOTAL DRAINAGE AREA OF LAKE =
                        SUM OF SUB-DRAINAGE AREAS   =
       557.1
       549.9
TOTAL FLOW IN  =
TOTAL FLOW OUT =
62.93
64.39
     MEAN MONTHLY FLOWS AND DAILY FLOWS(CMS)

TRIBUTARY   MONTH   YEAR    MEAN FLOW  DAY

1811A1
FLOW  DAY
                  FLOW  DAY
                                    FLOW
1811A2
6
7
8
9
10
11
12
1
2
3
4
5
6
7
8
9
10
11
12
1
2
3
4
5
73
73
73
73
73
73
73
74
74
74
74
74
73
73
73
73
73
73
73
74
74
74
74
74
9.628
3.115
2.973
1.699
1.841
4.248
11.327
19.255
9.911
11.327
12.176
7.646
6.881
2.461
2.353
1.201
1.280
2.973
7.929
13.451
7.051
8.042
8.552
5.409
9
8
12
9
16
10
9
12
9
10
7
12
9
8
12
9
16
10
9
12
9
10
7
12
11.044
3.115
7.362
1.614
1.869
1.841
3.681
4.814
9.345 24
8.495 17
13.026
10.477
7.872
2.209
5.125
1.133
1.303
1.274
2.605
3.398
6.598 24
5.947 17
9.146
7.391








11.327
10.336










8.099
7.362



-------
                                   TRIBUTARY FLOW INFORMATION FOR INDIANA
                                                                                          03/29/76
LAKE CODE 1811
GEIST RESERVOIR
     MEAN MONTHLY FLOWS AND DAILY FLOWS

TRIBUTARY   MONTH   YEAR    MEAN FLOW  DAY

181161
1811C1
181101
1811ZZ
6
7
8
9
10
11
12
I
2
3
4
5
6
7
8
9
10
11
12
1
2
3
4
5
6
7
8
9
10
11
12
1
2
3
4
5
6
7
8
9
10
11
12
1
2
3
4
5
73
73
73
73
73
73
73
74
74
74
74
74
73
73
73
73
73
73
73
74
74
74
74
74
73
73
73
73
73
73
73
74
74
74
74
74
73
73
73
73
73
73
73
74
74
74
74
74
0.309
0.051
0.045
0.011
0.011
0.074
0.340
0.595
0.311
0.368
0.368
0.241
0.425
0.147
0.144
0.074
0.079
0.178
0.481
0.821
0.425
0.481
0.538
0.340
0.368
0.076
0.071
0.020
0.023
0.108
0.425
0.736
0.396
0.453
0.481
0.311
0.595
0.212
0.201
0.102
0.110
0.255
0.680
1.161
0.595
0.680
0.736
0.453
9
8
12
9
16
10
9
12
9
10
7
12
9
10
12
9
16
10
9
12
9
10
7
12
9
8
12
9
13
10
9
12
9
10
7
12
9
a
12
9
13
10
9
12
9
10
7
12
                                FLOW  DAY
                                                  FLOW  DAY
                                                                    FLOW
0.340
0.040
0.224
0.008
0.011
0.011
0.054
0.099
0.283
0.266
0.396
0.340
0.481
0.119
0.311
0.068
0.082
0.074
0.159
0.207
0.396
0.368
0.566
0.453
0.425
0.062
0.278
0.017
0.023
0.023
0.085
0.136
0.368
0.311
0.510
0.396
0.680
0.190
0.453
0.096
0.110
0,110
0.224
0.283
0.566
0.510
0.793
0.623








24
17










24
17










24
17



10


16



24
17


                                                                    0.368
                                                                    0.340
                                                                    0.481
                                                                    0.453
                                                                    0.453
                                                                    0.396
                                                                    0.164
                                                                    0.113
                                                                    0.708
                                                                    0.623

-------
        APPENDIX D
PHYSICAL and CHEMICAL DATA

-------
STORET RETRIEVAL DATE 76/03/30
                                                                  181101
                                                                 39 55 59.0 085 56 17.0 3
                                                                 GEIST RESERVOIR
                                                                 18057   INDIANA
                                                                                          051992
DATE
FROM
TO
73/05/10


73/03/02

73/10/15



DATE
FROM
TO
73/05/10


73/08/02

73/10/15


TIME
OF
DAY
11 10
11 10
11 10
15 05
15 05
10 20
10 20
10 20

TIME
OF
DAY
11 10
11 10
11 10
15 05
15 05
10 20
10 20
10 20
DEPTH
FEET
0000
0006
0014
0000
0005
0000
0005
0008

DEPTH

FEET
0000
0006
0014
0000
0005
0000
0005
0008
00010
WATER
TEMP
CENT
18.2
18.1
17.5
26.2
25.8
19.9
19.6
19.6
00665
PHOS-TOT

MG/L P
0.089
0.050
0.067
0.179
0.157
0.095
0. 137
0.133
00300 00077 00094
DO TRANSP CNDUCTVY
SECCHI FIELD
MG/L INCHES MICROMHO

11.2
9.1

10.8

7.8
7.6
32217
CHLRPHYL
A
UG/L
54.2


94.1

70.4


21 590
580
580
14 491
489
24 444
458
456












HEPALES 2111202
0018 FEET DEPTH CLASS 00
00400 00410 00610 00625 00630 00671
PH T ALK NH3-N TOT KJEL N02&N03 PHOS-DIS
CAC03 TOTAL N N-TOTAL ORTHO
SU
8.20
8.30
8.10
8.60
8.50
8.40
8.40
8.30












MG/L
260
260
250
185
182
178
190
184












MG/L
0.060
0.060
0.080
0.030
0.080
0.120
0.090
0.070












MG/L
0.700
0.700
0.800
2.200
2.000
1.200
1.200
1.000












MG/L
2.220
2.240
2.210
0.330
0.400
0.080
0.120
0.080












MG/L P
0.013
0.008
0.009
0.027
0.015
0.015
0.016
0.015













-------
STORET RETRIEVAL DATE 76/03/30
                                                                  181102
                                                                 39 54 38.0 085 58 56.0 3
                                                                 GEIST RESERVOIR
                                                                 18097   INDIANA
                                                                                          051992
DATE
FROM
TO
73/05/10



73/08/02


73/10/15




DATE
FROM
TO
73/05/10



73/08/02


73/10/15



TIME DEPTH
OF
DAY FEET
11 45 0000
11 45 0004
11 45 0015
11 45 0020
14 55 0000
14 55 0005
14 55 0017
10 40 0000
10 40 0005
10 40 0010
10 40 0018

TIME DEPTH
OF
DAY FEET
11 45 0000
11 45 0004
11 45 0015
11 45 0020
14 55 0000
14 55 0005
14 55 0017
10 40 0000
10 40 0005
10 40 0010
10 40 0018
00010
WATER
TEMP
CENT
17.3
17.0
16.8
16.2
26.3
26.0
25.3
20.8
20.7
20.7
20.6
00665
PHOS-TOT

MG/L P
0.070
0.057
0.051
0.058
0.059
0.049
0.043
0.074
0.077
0.081
0.092
00300
DO

MG/L

9.9
9.6
7.8

8.8
3.4

6.8
6.8
7.0
32217
CHLRPHYL
A
UG/L
34.9



17.4


4.7



00077 00094
TRANSP CNDUCTVY
SECCHI FIELD
INCHES MICROMHO
34 530
540
540
560
40 444
442
453
32 391
393
394
392















11EPALES 2111202
0023 FEET DEPTH CLASS 00
00400 00410 00610 00625
PH T ALK NH3-N TOT KJEL

SU
8
8
8
8
8
8
7
8
8
8
8

















.40
.40
.30
.30
.50
.50
.70
.40
.30
.30
.30















CAC03
MG/L
198
198
196
197
159
160
163
151
155
152
152















TOTAL
MG/L
0.060
0.060
0.080
0.150
0.110
0.090
0.330
0.120
0.110
0.100
0.120















N
MG/L
0.700
0.600
0.700
0.700
.200
.100
.100
.000
.900
.000
.100















00630
N02&N03
N-TOTAL
MG/L
2.890
3.020
2.920
2.990
0.990
0.990
0.990
0.080
0.070
0.060
0.060















00671
PHOS-DIS
ORTHO
MG/L P
0.006
0.005
0.004
0.005
0.009
0*009
0.010
0.009
0.009
0.006
0.006
















-------
       APPENDIX E
TRIBUTARY and WASTEWATER
  TREATMENT PLANT DATA

-------
STORE! RETRIEVAL DATE 76/03/30
                                                                 39 53  55.0  085  59 29.0  4
                                                                 FALL CREEK
                                                                 18      7.5 MCCORDSVILLE
                                                                 0/GFIST  RES              051992
                                                                 79TH ST  6RDG BELO GEIST RES 0AM
                                                                 11EPALES             £111204
                                                                  0000  KEET   DEPTH  CLASS 00
DATE
FROM
TO
73/06/09
73/07/08
73/08/12
73/09/09
73/10/16
73/11/10
73/12/09
74/01/12
74/02/09
74/02/24
74/03/10
74/03/17
74/04/07
74/05/12
00630 00625
TIME DEPTH N020N03 TOT KJEL
OF N- TOTAL N
DAY FEET
10
11
10
14
18
11
10
10
14
13
10
10
15
14
40
00
?0
?5
45
30
45
20
40
00
00
30
10
10
MG/L
9.
2.
1.
0.
1.
1.
3.
3.
3.
4.
3.
2.
4.
3.
500
040
380
530
060
040
500
080
600
200
780
900
300
250
MG/L
1.
0.
3.
0.
0.
0.
1.
0.
0.
1.
0.
0.
0.
1.
500
350
400
320
400
250
000
400
200
700
400
600
900
100
00610 00671 00665
NH3-N PHOS-DIS PHOS-TOT
TOTAL UKTHO
MG/L
0.
0.
0.
u.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
050
024
060
015
023
009
032
056
030
090
030
025
020
125
MG/L
0.
3.

0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
p
054
031

032
057
017
02ft
044
020
100
020
020
035
050
MG/L P
0.115
0.045

0.055
0.085
0.040
0.028
0.055
0.030
0.150
0.055
0.070
0.070
0.170

-------
STORE! RETRIEVAL UATE 76/03/30
                                                                  ldllA2
                                                                 39 57 16.0  085 52 01.0 4
                                                                 FALL CHEEK
                                                                 18      7.5 INGALLS
                                                                 I/GE1ST KES              051992
                                                                 ST HkY 238  BRDG 2 MI  NNW OF FOKTVILLE
                                                                 11EPALES             2111204
                                                                  0000 FEET   DEPTH  CLASS 00
00630
DATE
FROM
TO
73/06/09
73/07/08
73/08/12
73/09/09
73/10/16
73/11/10
73/12/09
74/01/12
74/02/09
74/02/24
74/03/10
74/03/17
74/04/07
74/05/12
TIME DEPTH
OF
DAY
12
11
09
13
18
10
09
12
13
14
10
09
14
13
NI02&N03
N-TOTAL
FEET
35
30
10
45
05
38
45
25
45
10
00
30
?0
?0
MG/L
5
2
1
1
1
1
2
3
3
2
3
3
3
2
.400
.400
.340
.700
.460
.560
.520
.500
.400
.100
.300
.000
.600
.400
00625
TOT KJEL
N
MG/L
1.100
0.380
1.890
0.840
0.550
0.200
0.400
0.300
0.700
0.500
0.600
0.600
0.800
1.000
00610
NH3-N
TOTAL
MG/L
0
0
0
0
0
0
0
0
0
0
0
0
0
0
.069
.016
.061
.078
.039
.023
.048
.012
.055
.055
.025
.030
.030
.047
00671
PHOS-DIS
00665
PHOS-TOT
ORTHO
MG/L
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
P
052
075
110
096
115
084
048
020
030
155
0.035
0.
0.
0.
035
035
022
MG/L P
0
0

0
0
0
0
0
0
0
0
0
0
0
.140
.115

.150
.170
.102
.065
.030
.055
.175
.105
.090
.065
.120

-------
STORE! RETRIEVAL DATE 76/03/30
                                                                  1811B1
                                                                 39 54 05.0 085 57 50.0 4
                                                                 DRY BRANCH
                                                                 18      7.5 MCCORDSVILLE
                                                                 T/GEIST  RES              051992
                                                                 FOX RL) BKDG 1.5 MI N OF OCKLANDON
                                                                 11EPALES             2111204
                                                                  0000 FEET  DEPTH  CLASS 00
DATE
FROM
TO
73/06/09
73/07/08
73/08/12
73/09/09
73/10/16
73/11/10
73/12/09
74/01/12
74/02/09
74/02/24
7W03/10
74/03/17
74/04/07
74/05/12
00630 00625
TIME DEPTH N02&N03 TOT KJEL
OF N-TOTAL N
DAY FEET
11
10
10
14
18
11
10
11
14
13
10
09
14
13
45
?0
07
10
30
10
35
15
30
30
30
10
50
45
MG/L
10
4
1
0
0
1
4
5
5
4
<+
4
5
7
.600
.600
.000
.051
.790
.510
.600
.600
.000
.100
.900
.700
.460
.500
MG/L
6.
0.
1.
1.
0.
0.
0.
0.
0.
0.
0.
0.
0.
2.
400
790
540
760
750
650
500
400
700
800
500
600
400
500
00610 00671 00665
NH3-N PHOS-DIS PHOS-TOT
TOTAL ORTHO
MG/L
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
480
042
150
165
020
039
096
008
030
090
025
025
005K
560
MG/L P
0.079

0.680
0.236
0.510
0.580
0.080
0.020
0.050
0.090
0.085
0.085
0.025
0.230
MG/L P
0

0
0
0
0
0
0
0
0
0
0
0
0
.125

.880
.500
.620
.605
.105
.030
.075
.165
.130
.128
.030
.350
    K VALUE KNOWN TO BE
    LESS THAN INDICATED

-------
STORE! RETRIEVAL DATE 76/03/30
                                                                  1811C1
                                                                 39 56 30.0 085 52 30.0 4
                                                                 FLATFORK CHEEK
                                                                 18      7.5 MCCOROSVILLE
                                                                 T/GEIST RES-              051992
                                                                 CONNECTICUT AVE BRDG 1.5 MI W OF FOKTVIL
                                                                 11EPALES             2111204
                                                                  0000 FEET  DEPTH  CLASS 00
DATE
FROM
TO
73/07/10
73/08/12
73/09/09
73/10/16
73/11/10
73/12/09
74/01/12
74/02/09
74/02/24
74/03/10
74/03/17
74/04/07
74/05/12
00630 00625
TIME DEPTH N02&N03 TOT KJEL
OF N-TOTAL N
DAY FEET
16
09
13
18
10
09
12
13
13
11
12
14
13
00
15
50
10
45
55
00
50
30
00
00
25
25
MG/L
1
1
1
1
1
2
4
3
4
3
2
3
3
.980
.320
.500
.200
.440
.400
.100
.200
.100
.000
.900
.200
.600
MG/L
0.
1.
0.
0.
0.
0.
0.
0.
1.
0.
0.
0.
0.
480
260
460
400
150
500
500
300
000
400
500
500
900
00610 00671 00665
NH3-N PHOS-DIS PHOS-TOT
TOTAL ORTHO
MG/L
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
031
052
044
006
009
026
068
005
110
010
010
010
060
MG/L
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
P
023
073
046
039
016
024
068
015
090
020
050
017
025
MG/L P
0.055

0.070
0.075
0.020
0.030
0.095
0.025
0.140
0.050
0.055
0.040
0.105

-------
STORE! RETRIEVAL DATE 76/03/30
                                                                  1H1101
                                                                 39  57  17.0  085  54  31.0  4
                                                                 THORPE CREEK
                                                                 18       7.5 MCCOWOSVILLE
                                                                 T/GEIST  RES              051992
                                                                 E 113TH  ST  BRDG 3.5 MI  WNM  OF  FORTVILLE
                                                                 HEPALES             2111204
                                                                  0000 FEET  DEPTH  CLASS  00
DATt
FROM
TO
73/06/09
73/07/08
73/08/12
73/09/09
73/10/13
73/11/10
73/12/09
74/01/12
74/02/09
74/02/24
74/03/10
7W03/17
74/04/07
74/05/12
00630 00625
TIME DEPTH N02&N03 TOT KJEL
OF N-TOTAL N
DAY FEET
12
11
09
13
07
10
09
10
13
13
10
11
14
13
05
00
05
40
50
30
30
25
30
40
45
30
10
15
MG/L
9.
4.
2.
0.
0.
1.
5.
2.
5.
4.
6.
6.
6.
5.
900
300
200
770
610
430
040
900
700
100
300
100
800
200
MG/L
1.
0.
2.
1.
0.
0.
0.
0.
0.
1.
0.
0.
0.
1.
320
540
310
000
780
300
300
300
200
000
400
400
600
200
00610 00671 00665
NH3-N PHOS-DIS PHOS-TOT
TOTAL ORTHO
MG/L
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
082
066
110
058
044
007
008
016
012
130
010
010
005
030
MG/L
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
p
065
042
220
037
063
014
020
020
015
090
020
020
020
010
MG/L P
0.105
0.065
0.560
0.125
0.105
0.025
0.025
0.020
0.020
0.140
0.035
0.030
0.035
0.060

-------
STORE! RETRIEVAL DATE 76/03/30
                                                                  IflllXA          P01611XA     P000125
                                                                 40 00 30.0 085 30 30.0 4
                                                                 SHENANOOAH HI  SCHOOL
                                                                 18      HENRY  CO HWY MAP
                                                                 T/GEIST RESERVOIR        051991
                                                                 SUGAR CREEK
                                                                 11EPALES             2141204
                                                                  0000 FEET  DEPTH  CLASS 00
DATE
FROM
TO
73/06/29
73/07/30
73/08/29
73/09/24
73/10/31
73/11/28
73/12/17
74/01/16
74/02/20
74/03/25
74/04/23
74/05/22
74/06/14
00630 00625 00610 00671 00665 50051 50053
TIME DEPTH N02&N03 TOT KJEL NH3-N PHOS-DIS PHOS-TOT FLOW CONDUIT
OF N-TOTAL N TOTAL ORTHO RATE FLOW-MGD
DAY FEET MG/L MG/L MG/L MG/L P MG/L P INST MGD MONTHLY
08 35 0.210 2.300 0.084 5.430 5.800
08 35 0.160 1.900 0.042 3.700 4.100
12
11
09
13
11
13
10
15
07
12
14
30
30
15
00
45
45
30
00
00
30
00

0
0
4
3
9
4
4
2
3

.150
.530
.400
.300
.950
.700
.300
.160
.700
4.200
1.900
1.000
0.600
0.930
0.700
0.500K
l.OOOK
l.OOOK
2.400
l.OOOK
l.OOOK
0.132
0.450
0.010K
0.068
0.063
0.040
0.050K
0.050K
0.063
0.050K
0.050K
2.980
3.990
1.380
2.100
2.900
2.670
2.500
0.840
1.150
0.470
0.434
3.500
4.000
1.550
2.400
3.400
2.900
2.700
1.100
1.300
0.570
0.470

0.003
0.003
0.003
0.003
0.003
0.003
0.003
0.003
0.003
0.003

0
0
0
0
0
0
0
0
0
0

.003
.003
.003
.003
.003
.003
.003
.003
.003
.003
    K  VALUE KNOWN  TO tiE
    LESS  THAN  INDICATED

-------
STORET RETRIEVAL DATE 76/03/30
                                                                  1811CA          TF1811CA     P002480
                                                                 39 26 05.0 085 51 50.0 4
                                                                 FORTVILLE
                                                                 18      7.5 INGALLS
                                                                 T/6EIST RESERVOIR        051891
                                                                 FLATFORK CREEK
                                                                 11EPALES             2141204
                                                                  0000 FEET  DEPTH  CLASS 00
DATE
FROM
TO
73/06/29
73/07/30
73/09/07
73/09/28
73/10/29
73/11/30
73/12/24
74/03/13
74/04/15
74/06/26
74/07/12
74/08/08
00630
TIME DEPTH N02&N03
OF N-TOTAL
DAY FF.ET
10
09
08
08
10
10
08
14
09
09
08
08
30
30
00
30
30
00
00
00
00
00
30
00
MG/L
2.
1.
0.
1.
0.
2.
1.
0.
2.
3.
1.
0.
730
980
510
380
315
900
000
160
160
780
080
800
00625
TOT KJEL
N
MG/L
5.510
6.200
10.300
15.000
16.500
4.700
7.000
6.800
12.000
2.700
3.500
12.000
00610 00671 00665
NH3-N PHOS-DIS PHOS-TOT
TOTAL ORTHO
MG/L
0.120
0.050
0.410
1.440
3.300
0.057
0.048
0.050K
4.100
0.085
0.740
1.250
MG/L P
1.000
1.050
2.020
2.800
2.920
0.590
1.200
0.120
5.800
0.450
1.100
1.350
50051 50053
FLOW CONDUIT
RATE FLOw-MGD
MG/L P INST
1.650
1.750
2.600
3.700
4.300
0.860
1.650
2.400
15.700
0.560
1.350
2.000
0
0
0
0
0
0
0
0
0
0
0
0
MGD MONTHLY
.659
.397
.379
.361
.300
.700
.500
.719
.670
.711
.500
.300
0.500
0.300
0.420
0.400
0.300
0.400
0.500
0.700
0.690
0.689
0.600
0.400
   K VALUE KNOWN TO BE
   LEbS THAN INDICATED

-------
STORET RETRIEVAL DATE 76/03/30
                                                                  1811AC          TF1B11AC     P002300
                                                                 40 03 10.0 085 32 15.0 4
                                                                 MIDOLETON
                                                                 18      7.5 MIOOLETON
                                                                 T/GEIST RESERVOIR        051991
                                                                 FALL CREEK
                                                                 11EPALES             2141204
                                                                  0000 FEET  DEPTH  CLASS 00
DATE
FROM
TO
73/06/12
CP(T)-
73/06/12
73/07/10
CP(T)-
73/07/10
73/08/15
73/09/12
CP-
73/09/12
73/10/09
CP-
73/10/09
73/11/12
CP(T)-
73/11/12
73/12/14
7^/01/17
CP
-------
STORET RETRIEVAL DATE 76/03/30
                                                                  1811AB          ASiailAB     P002496
                                                                 40  00  00.0  085 45 00.0  4
                                                                 PENOLETON
                                                                 18       7.5 PENOLETON
                                                                 T/GEIST RESERVOIR        051991
                                                                 FALL CREEK
                                                                 11EPALES             2141304
                                                                  0000  FEET   DEPTH  CLASS 00
DATE
FROM
TO
73/06/10
CP(T)-
73/06/10
73/07/20
CP(T)-
73/07/20
73/09/20
CP-
73/09/20
73/11/01
CP(T>-
73/11/01
73/12/05
CP(T>-
73/12/05
74/01/04
CPU>-
74/01/04
74/02/05
CP(T>-
74/02/05
74/03/05
CP(T>-
74/03/05
74/04/03
CP(T>-
74/04/03
74/05/08
CP(T)-
74/05/08
74/06/07
CP(T>-
74/06/07
74/07/11
74/08/02
00630
TIME DEPTH N026.N03
OF N-TOTAL
DAY FEET MO/L
06

23
08

20
07

23
07

22
07

22
07

13
07

22
08

23
08

22
08

23
08

22
11
14
00

00
00

00
00

00
00

00
00

00
00

00
00

00
00

00
00

00
00

00
00

00
00
00

0


0


0


0


0


0


0


1


0


0


0

0
0

.088


.250


.086


.190


.390


.700


.160


.840


.400


.080


.120

.040
.240
00625
TOT KJEL
N
MG/L

13.200


16.000


10.500


22.000


14.000


12.500


12.000


5.600


6.000


18.000


12.000

9.300
19.000
00610 00671 00665 500S1 50053
NH3-N PHOS-DIS PHOS-TOT FLOW CONDUIT
TOTAL ORTHO RATE FLOW-MOD
MG/L MG/L P MG/L P INST MOD MONTHLY

0


0


3


4


0


0


0


0


0


3


0

0
14

.100


.180


.025


.400


.019


.040K


.920


.050K


.110


.100


.530

.560
.000

2.600


2.260


4.020


3.360


2.500


1.600


2.700


1.050


1.300


2.000


2.100

0.710
3.200

3.300


3.800


5.100


5.100


3.200


2.700


5.500


1.050


1.800


4.300


2.700

1.350
4.400

0.255


0.201


0.176


0.167


0.181


0.173


0.203


0.610


0.570


0.183


0.136

0.170
0.122

0.300


0.208


0.180


0.172


0.172


0.186


0.310


0.287


0.315


0.283


0.188

0.275
0.151
   K VALUE KNOWN TO BE
   LESS THAN INDICATED

-------
STORE! RETRIEVAL DATE 76/03/30
DATE
FROM
TO
73/06/05
cpm-
73/06/05
73/07/03
CP(T>-
73/07/03
63/11/08
CP(T)-
73/10/09
73/12/18
CP(T)-
73/12/19
74/01/30
cpm-
74/01/30
74/02/27
cpm-
74/02/28
74/07/24
CPU)-
74/07/24
00630 00625 00610 00671
TIME DEPTH N02&N03 TOT KJEL NH3-N PHOS-DIS
OF N-TOTAL N TOTAL ORTHO
DAY FEET MG/L MG/L MG/L MG/L P
08 00
0.820 3.000 0.350 1.680
20 00
08

20
17

05
17

05
06

18
10

10
09

22
00

00
00

00
00

00
00

00
00

00
00

00

0


5


2


2


5


4


.890


.900


.200


.320


.040


.300


1.



980 •


2.300


2.


2.


1.


1.



900


000


700


OOOK


0


0


0


0


0


0


.190


.120


.240


.210


.140


.088


1



.510


2.700


2


3


2


2



.500


.200


.300


.600

                                                                  1811AA          AS1811AA     P002300
                                                                 39 59 00.0  085 46 00.0  4
                                                                 PENDLETON STATE REFORMATORY
                                                                 18      7.5 INGALLS
                                                                 T/GEIST RESERVOIR        051992
                                                                 FALL CREEK
                                                                 11EPALES             2141204
                                                                  0000 FEET   DEPTH  CLASS 00

                                                              00665     50051     50053
                                                            PHOS-TOT    FLOW    CONDUIT
                                                                        RATE    FLOw-MGO
                                                             MG/L P   INST MGD  MONTHLY
                                                               2.000      0.300      0.250
                                                               1.870     0.200     0.250
                                                               3.500     0.500     0.420
                                                               3.200     0.350     0.375
                                                               4.700     0.330     0.450
                                                               2.600     0.350     0.450
                                                               3.000     0.400     0.400
  K VALUE KNOWN TO dE
  LESS THAN  INDICATED

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