U.S. ENVIRONMENTAL PROTECTION AGENCY
               NATIONAL EUTROPHICATION SURVEY
                        WORKING PAPER SERIES
                                              REPORT
                                               ON
                                          PERRY RESERVOIR
                                          JEFFERSON COUNTY
                                              KANSAS
                                           EPA REGION VII
                                        WORKING PAPER No,  521
     CORVALLIS ENVIRONMENTAL RESEARCH LABORATORY - CORVALLIS, OREGON
                                 and
    ENVIRONMENTAL MONITORING & SUPPORT LABORATORY - LAS VEGAS, NEVADA
TwTG.P.O. 699-440

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                                     REPORT
                                       ON
                                PERRY RESERVOIR
                                JEFFERSON COUNTY
                                     KANSAS
                                 EPA REGION VII
                             WORKING PAPER No,  521
        WITH THE COOPERATION OF THE
KANSAS DEPARTMENT OF HEALTH AND ENVIRONMENT
                  AND THE
           KANSAS NATIONAL GUARD
                 MAY, 1977

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                                   CONTENTS

                                                               Page

  Foreword                                                      ii

  List of Kansas Study Reservoirs                               iv

  Lake and Drainage Area Map                                     v


  Sections
                                                          •
  I.   Conclusions                                                1

 II.   Lake and Drainage Basin Characteristics                    4

III.   Lake Water Quality Summary                                 5

 IV.   Nutrient Loadings                                         10

  V.   Literature Reviewed                                       16

 VI.   Appendices                                                17

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                                 ii
                          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 freshwater 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)], 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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                                 Ill
    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
freshwater 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 Kansas State Department of
Health and Environment for professional involvement, to the Kansas
National Guard for conducting the tributary sampling phase of
the Survey, and to those Kansas wastewater treatment plant opera-
tors who voluntarily provided effluent samples and flow data.

    The staff of the Kansas Division of Environmental Health pro-
vided invaluable lake documentation and counsel  during the Survey,
reviewed the preliminary reports,  and provided critiques most use-
ful in the preparation of this Working Paper series.

    Major General Edward R. Fry, the Adjutant General of Kansas,
and Project Officer Colonel Albin L. Lundquist,  who directed the
volunteer efforts of the Kansas National  Guardsmen, are also grate-
fully acknowledged for their assistance to the Survey.

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                                    1v


                      NATIONAL EUTROPHICATION SURVEY

                             STUDY RESERVOIRS

                             STATE OF KANSAS

NAME                                                         COUNTY

Cedar Bluff                                                  Trego
Council Grove                                                Morris
Elk City                                                     Montgomery
Fall River                                                   Greenwood
John Redmond                                                 Coffey, Lyon
Kanopolis                                                    Ellsworth
Marion                                                       Marion
Melvern                                                      Osage
Mil ford                                                      Clay, Geary
Norton                                                       Norton
Perry                                                        Jefferson
Pomona                                                       Osage
Toronto                                                      Greenwood, Woodson
Tuttle Creek                                                 Marshall, Potta-
                                                              watomie, Riley
Wilson                                                       Russell

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                      LSobetho
                                                                        Kan.
                                                                      Map Location
             WetmoreX
               -v'^
) N-  LKt,ncroh       "  ^

\     N  N v
           PERRY RESERVOIR
         ®   Tributary Sampling Site
         X   I aki.' Jamplinq Site
         ^   Sewage Treatment Facility
         10   Drainage Area Boundary
              Land Subject to Inundation
                                     »o Km.
                    Sc
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                             PERRY RESERVOIR
                             STORE! NO.  2011

I.   CONCLUSIONS
    A.   Trophic Condition:
            Survey data indicate that Perry Reservoir is potentially
        eutrophic.  However,  the reservoir becomes quite turbid during
        periods of runoff,  and primary productivity is intermittently
        light-limited (Kring,  1977).
            This water body ranked ninth in overall trophic quality
        when the 15 Kansas  reservoirs sampled in 1974 were compared
        using a combination of six water quality parameters*.   Seven
        of the reservoirs had  less median total  phosphorus, eight had
        less median dissolved  orthophosphorus,  11  had less and  one had
        the same median inorganic nitrogen, two had less mean chlorophyll
        £,  and six had greater mean Secchi disc transparency.   Depression
        of dissolved oxygen with depth occurred at all  sampling stations
        in June.
            Survey limnologists did not observe any nuisance conditions
        during their sampling  but did note that the reservoir was quite
        turbid at times.
    B.   Rate-Limiting Nutrient:
            The algal  assay results indicate that  Perry Reservoir was
        phosphorus limited  at  the time the sample  was collected (02/12/74),
  See Appendix A.

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    The reservoir data indicate phosphorus limitation at all
    sampling stations and times.  However, because of turbidity,
    primary productivity in the reservoir is intermittently light-
    limited rather than nutrient-limited.
C.   Nutrient Controllability:
        1.  Point sources--During the sampling year,  the listed
    point sources accounted for 18.0% of the total phosphorus load to
    Perry Reservoir.  The wastewater treatment plant  at Morton con-
    tributed 7.4%, the facility at Holton contributed 7.2%, the plant
    at Wetmore contributed 0.4%, and the remaining four plants were
    estimated to have collectively contributed 3.0%.
        The present phosphorus loading of 2.07 g/m2/year is 4.7
    times that proposed by Vollenweider (Vollenweider and Dillon,
    1974) as a eutrophic loading (see page 15).   Even though nutrient-
    wise the reservoir is phosphorus-limited, reduction of the point-
    source phosphorus loads may not result in a significant improve-
    ment of the trophic condition because of light-limitation.  In
    a previous report it is noted that while nutrient levels in
    Perry Reservoir are high, aquatic growths are not excessive due
    to high turbidity resulting from soil erosion in  the drainage
    of the reservoir (Anonymous, 1975).  However, if  soil conservation
    projects are initiated to reduce erosion and the  resulting tur-
    bidity in the reservoir, the present phosphorus loading is likely
    to result in the development of nuisance aquatic  vegetation.

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    2.  Non-point sources--Non-point sources contributed 82.0%
of the total phosphorus load during the sampling year.   The
Delaware River contributed 71.0%,  Slough Creek contributed 1.3%,
Little Slough Creek contributed 0.4%, and Rock Creek contributed
0.8%.  Ungaged minor tributaries and immediate drainage contributed
an estimated 7.6%.

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II.   RESERVOIR AND DRAINAGE BASIN CHARACTERISTICS1"

     A.   Morphometry  :

         1.  Surface area:  49.37 kilometers2.

         2.  Mean depth:  3.7 meters.

         3.  Maximum depth:  11.9 meters.

         4.  Volume:  182.669 x 106 m3.

         5.  Five-year median hydraulic  retention time:   281  days.

     B.   Tributary and Outlet:
         (See Appendix C for flow data)

         1.  Tributaries -

                                               Drainage        Mean  flow
             Name                              area (km2)*    (m3/sec)*

             Delaware River (at A-3)             1,942.5         9.110
             Slough Creek                          109.8         0.650
             Little Slough Creek                    47.1         0.088
             Rock Creek (at E-2)                    35.5         0.200
             Minor tributaries &
              immediate drainage -                 708.7         3.472

                            Totals               2,843.6         13.520**

         2.  Outlet -

             Delaware River                      2,893.0***      12.710

     C.   Precipitation****:

         1.  Year of sampling:  75.3 centimeters.

         2.  Mean annual:  92.4 centimeters.
 t Table of metric conversions—Appendix B.
 tt Kring, 1977.
 * For limits of accuracy, see Working Paper No.  175,  "...Survey Methods,
   1973-1976".
 ** Total inflow adjusted to equal outflow plus evaporation loss.
 *** Includes area of reservoir.
 **** See Working Paper No. 175.

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III.   WATER QUALITY SUMMARY
      Perry Reservoir was sampled three times during the open-water
  season of 1974 by means of a pontoon-equipped Huey helicopter.   Each
  time,  samples for physical  and chemical  parameters were collected
  from a number of depths at four stations in April  and five stations
  in  June and October (see map,  page v).   During each visit,  a  single
  depth-integrated (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 
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PARAMETER

TEMP (C)

DISS OXY (MG/L)

CNOCTVY (MCROMO)

PH  (STAND UNITS)

TOT ALK (MG/L)

TOT P (MG/L)

ORTHO P (MG/L)

N02+N03 (MG/L)

AMMONIA (MG/D

KJEL N  (MG/L)

INORG N (MG/L)

TOTAL N (MG/L)

CHLRPYL A (UG/L)

SECCHI  (METERS)
      A.  SUMMARY OF PHYSICAL AND


      1ST SAMPLING (  4/12/74)

            4 SITES

    RANGE        MEAN   MEDIAN

10.0  -  11.7    10.7    10.6

 9.2  -  10.4     9.9    10.0
8.3
167.
0.037
0.008
0.450
0.040
0.400
0.580
1.060
5.1
0.5
8.4
- 204.
- 0.064
- 0.035
- 1.140
- 0.130
- 0.800
- 1.220
- 1.640
- 13.2
0.8
8.3
178.
0.053
0.020
0.849
0.082
0.572
0.931
1.422
8.7
0.6
8.3
174.
0.056
0.017
0.905
0.075
0.600
0.975
1.450
8.3
0.6
CHEMICAL CHARACTERISTICS FOR PERRY RESERVOIR
 STORE? CODE 2011

           2ND SAMPLING ( 6/25/74)

                 5 SITES

         RANGE

     19.9  -  26.8

      1.6  -  14.2

     371.  -  423.

      7.9  -   8.7

     142.  -  171.

    0.032  - 0.149

    0.011  - 0.051

    0.850  - 1.960

    0.040  - 0.190

    0.300  - 0.300

    0.920  - 2.070

    1.250  - 2.440

      0.9  -   4.9

      0.3  -   0.6
                                                                                                          3RD  SAMPLING  (10/  2/74)

                                                                                                                5  SITES
MEAN
23.2
5.2
395.
6.2
161.
0.074
0.026
1.372
0.077
0.443
1.449
1.816
2.9
0.5
MEDIAN
23.3
5.4
396.
8.2
161.
0.064
0.022
1.250
0.070
0.400
1.300
1.660
2.9
0.6
RANGE
15.9
7.8
167.
7.8
162.
0.035
0.011
0.540
0.020
0.200
0.600
1.040
1.9
0.5
- 17.6
9.0
- 337.
8.2
- 172.
- 0.096
- 0.020
- 0.880
- 0.060
- 0.900
- 0.910
- 1.530
- 12.8
0.7
MEAN
17.0
8.3
317.
8.1
165.
0.052
0.015
0.768
0.033
0.445
0.801
1.213
5.8
0.5
MEDIAN
17.2
8.4
331.
8.1
164.
0.049
0.015
0.800
0.030
0.450
0.830
1.200
5.2
0.5

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B.   Biological  Characteristics:

    1.   Phytoplankton -
        Sampling
        Date

        04/12/74
        06/25/74
        10/02/74
Dominant
Genera
1.
2.
3.
4.
5.
1.
2.
3.
4.
5.
1.
2.
3.
4.
5.
Stephanodiscus sp.
Chroomonas sp.
Melosira sp.
Cryptomonas sp.
Chlorococcol cells
Other genera
Total
Cryptomonas sp.
Flagellates
Trachelomonas sp.
Chroomonas sp.
Coelastrum sp.
Other genera
Total
Chroomonas sp.
Melosira sp^.
Nitzschia sp.
Cryptomonas sp.
Skeletonema sp.
Other genera
Algal Units
per ml	

      891
      806
      806
      127
      127
      338
                                          Total
    3,095

      368
      221
      184
      147
       37
      146

    1,103

      741
      456
      456
      285
      114
      341

    2,393

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                                 8
C.



Sampling
Date
04/12/74
06/25/74
10/02/74
Dominant
Genera
1
2
3
4
5
1
2
3
4
5
1
2
3
4
5
Chlorophyll a
(ug/D
5.1
13.2
9.6
7.1
4.3
4.9
1.5
0.9
2.9
3.0
5.2
6.2
12.8
1.9
Limiting Nutrient Study:
1.

2.

Autoclaved, filtered,
Ortho
Spike (mg/1) Cone.
Control 0.
0.050 P 0.
0.050 P + 1.0 N 0.
1.0 N 0.
Discussion -
The control yield
and nutrient spiked -
P Inorganic N
(mg/1) Cone, (mg/1)
010 0.791
060 0.791
060 1.791
010 1.791


Maximum yield
(mg/1 -dry wt. )
7.4
25.0
34.9
6.5

of the assay alga, Selenastrum capri-
cornutum, indicates that the potential primary
productivity
        of Perry Reservoir was high at the time  the  sample was col-
        lected (04/12/74).   Also,  the increase in yield with the

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addition of phosphorus alone indicates that the reservoir
was phosphorus limited at that time.   Note that the addition
of nitrogen alone resulted in a yield no greater than that
of the control.
    The reservoir data also indicate phosphorus limitation.
The mean inorganic nitrogen/orthophosphorus ratios were 36/1
or greater at all sampling stations and times, and phosphorus
limitation would be expected.  However, primary productivity
in the reservoir is intermittently light-limited rather than
nutrient-limited (Kring, 1977).

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                                     10
IV.   NUTRIENT LOADINGS
     (See Appendix E for data)
     For the determination of nutrient loadings,  the Kansas  National
 Guard collected monthly near-surface grab samples from each of the
 tributary sites indicated on the map (page v),  except for the months
 of May, June, and July when two samples were collected at most of the
 sites.  Sampling was begun in October,  1974, and was completed in
 September, 1975.
     Through an interagency agreement, stream flow estimates for the
 year of sampling and a "normalized" or average  year were provided by
 the Kansas District Office of the U.S.  Geological Survey for the
 tributary sites nearest the reservoir.
     In this report, nutrient loads for sampled  tributaries  were
 calculated using mean annual concentrations and mean annual flows.
 Nutrient loads shown are those measured minus point-source  loads,
 if any.
     Nutrient loads for unsampled "minor tributaries and immediate
 drainage" ("ZZ" of U.S.G.S.) were estimated using the mean  concen-
 trations in Brush Creek at station D-l  and the  mean annual  ZZ flow.
     The operators of the Everest, Hoi ton, Morton, and Wetmore waste-
 water treatment plants provided monthly effluent samples and corres-
 ponding flow data.  The operators of the wastewater treatment plants
 of Denison,  Oskaloosa, and Valley Falls did not participate; nutrient
 loads from these sources were estimated at 1.134 kg P and 3.401  kg

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                                    11
N/capita/year, and flows were estimated at 0.3785 m3/capita/day.

    A.  Waste Sources:

        1.   Known municipal* -
        Name

        Denison
        Everest
        Hoi ton
        Morton
        Oskaloosa
        Valley Falls
        Wetmore
        2.  Known industrial -
        Name

        Meat Packing Plant,
         Hoi ton**
Pop.
Served
278
359
3,369
2,385
1,005
1,291
415

Treatment
stab, pond
stab, pond
tr. filter
tr. filter
stab, pond
stab, pond
tr. filter
Mean Flow
(ms/d)
105.2
113.1
1,817.7
2,205.9
380.4
488.6
98.3
Receiving
Water
North Cedar Creek
Grasshopper Creek
Elks Creek
Delaware River
Big Slough Creek
Delaware River
Spring Creek
Treatment
Mean Flow
(m3/d)
anaerobic -
 aerobic ponds
Receiving
Water

Elks Creek
* Treatment plant questionnaires.
** Not in operation during the sampling year.

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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) -

                Delaware River (A-3)           72,665         71.0
                Slough Creek                    1,360          1.3
                Little Slough Creek               455          0.4
                Rock Creek (E-2)                  775          0.8

            b.  Minor tributaries & immediate
                 drainage (non-point load) -    7,775          7.6

            c.  Known municipal STP's -

                Denison                           315          0.3
                Everest                           165          0.2
                Holton                          7,385          7.2
                Horton                          7,615          7.4
                Oskaloosa                       1,140          1.1
                Valley Falls                    1,465          1.4
                Wetmore                           370          0.4

            d.  Septic tanks - Unknown            ?

            e.  Known industrial - None

            f.  Direct precipitation* -           865          0.9

                        Total                  102,350        100.0

        2.  Outputs -

            Reservoir outlet - Delaware River  24,850

        3.  Net annual P accumulation - 77,500 kg.
* 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) -

                Delaware River (A-3)          473,270         60.9
                Slough Creek                   24,520          3.2
                Little Slough Creek             5,325          0.7
                Rock Creek (E-2)               10,695          1.4

            b.  Minor tributaries & immediate
                 drainage (non-point load) -  172,670         22.2

            c.  Known municipal STP's -

                Denison                           945          0.1
                Everest                           360         <0.1
                Hoi ton                         11,395          1.5
                Horton                         16,110          2.1
                Oskaloosa                       3,420          0.4
                Valley Falls                    4,390          0.6
                Wetmore                           480         <0.1

            d.  Septic tanks - Unknown            ?

            e.  Known industrial - None

            f.  Direct precipitation* -        53,300          6.9

                        Total                 776,870        100.0

        2.  Outputs -

            Reservoir outlet - Delaware River 515,860

        3.  Net annual N accumulation - 261,010 kg.
* See Working Paper No.  175.

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                                14
D.   Non-point Nutrient Export by Subdrainage Area:

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

    Delaware River (A-3)                      37             244
    Slough Creek                              12             223
    Little Slough Creek                       32             375
    Rock Creek (E-2)                          22             301

E.   Mean Nutrient Concentrations in Ungaged Streams:

                                          Mean Total  P   Mean Total N
    Tributary                             Cone,  (mg/1)   Cone,  (mg/1)

    Brush Creek                               0.071           1.577
    Evans Creek                               0.066           0.817
    Fishpond Creek                            0.139           2.279

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                                15
F.   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             2.07       1.57        15.7       5.3
    Vollenweider phosphorus loadings
     (g/m2/yr)  based on mean depth and 5-year median
     hydraulic  retention time of Perry Reservoir:
        "Dangerous"  (eutrophic loading)            0.44
        "Permissible"  (oligotrophic loading)      0.22

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                                    16
V.  LITERATURE REVIEWED

    Anonymous, 1975.  Final environmental statement: Operation and
        maintenance, Perry Lake, Kansas.  U.S. Army Engr. Distr.,
        Kansas City, MO.

    Kring, R. Lynn, 1977.  Personal communication (revised reservoir
        morphometry; primary productivity).  KS Dept. of Health &
        Environment, Topeka.

    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.

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                                  17
VI.  APPENDICES
                                  APPENDIX A
                                 LAKE RANKINGS

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LAKE DATA TO BE USED IN RANKINGS
LAKE
CODE  LAKE NAME
2001  CEDAR BLUFF RESERVOIR
2002  COUNCIL GROVE
2003  ELK CITY
2004  FALL RIVER RESERVOIR
2005  JOHN REDMOND RESERVOIR
2006  KANOPOLIS RESERVOIR
2007  MARION RESERVOIR
2008  MELVERN RESERVOIR
2009  MILFORn RESERVOIR
2010  NORTON RESERVOIR
2011  PERRY RESERVOIR
2012  POMONA RESERVOIR
2013  TORONTO RESERVOIR
2014  TUTTLE CREEK RESERVOIR
2015  WILSON RESERVOIR
MEDIAN
TOTAL P
0.017
0.069
0.030
0.053
0.118
0.056
0.052
0.034
0.079
0.122
0.055
0.040
0.067
0.162
0.023
MEDIAN
INORG N
0.055
0.830
0.590
0.470
1.250
0.640
0.430
0.265
0.710
0.110
0.970
1.240
0.425
0.970
0.265
500-
MEAN SEC
431.667
485.889
490.400
488.667
492.667
487.000
483.667
459.111
^466.333
476.750
478.571
481.333
488.500
470.667
445.222
MEAN
CHLORA
4.217
9.789
3.212
7.683
9.467
16.033
12.400
30.400
18.883
21.360
5.614
8.312
6.583
11.278
8.867
15-
MIN DO
10.800
10.400
14.000
9.200
8.200
10.200
9.000
14.400
12.8CO
8.000
13.400
13.000
13.000
13.600
13.400
MEDIAN
DISS ORTHO P
0.004
0.028
0.003
0.016
0.066
0.011
0.010'
0.007
0.036
0.036
0.017
0.021
0.011
0.067
0.004

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LAKES RANKED BY INDEX NOS.
RANK  LAKE CODE  LAKE NAME               INDEX NO

   1  2001       CEDAR BLUFF RESERVOIR      539
   2  2015       WILSON RESERVOIR           439
   3  2007       MARION RESERVOIR           357
   4  2003       ELK CITY                   350
   5  2004       FALL RIVER RESERVOIR       328
   6  2008       MELVERN RESERVOIR          326
   7  2013       TORONTO RESERVOIR          303
   8  2010       NORTON RESERVOIR           292
   9  2011       PERRY RESERVOIR            279.
  10  2006       KANOPOLIS RESERVOIR        271
  11  2012       POMONA RESERVOIR           267
  12  2002       COUNCIL GROVE              230
  13  2009       MILFORD RESERVOIR          214
  14  2005       JOHN REDMOND RESERVOIR     164
  15  2014       TUTTLE CREEK RESERVOIR     139

-------
PERCENT OF LAKES WITH HIGHER VALUES (NUMBER OF LAKES WITH HIGHER VALUES)

LAKE
CODE  LAKE NAME

2001  CEDAR BLUFF RESERVOIR

2002  COUNCIL GROVE

2003  ELK CITY

2004  FALL RIVER RESERVOIR

2005  JOHN REDMOND RESERVOIR

2006  KANOPOLIS RESERVOIR

2007  MARION RESERVOIR

200fl  MELVERN RESERVOIR

2009  MILFORO RESERVOIR

2010  NORTON RESERVOIR

2011  PERRY RESERVOIR

2012  POMONA RESERVOIR

2013  TORONTO RESERVOIR

2014  TUTTLE CREEK RESERVOIR

2015  WILSON RESERVOIR
MEDIAN!
TOTAL P
100 <
29 (
86 <
57 (
14 (
43 (
64 (
79 (
21 1
7 1
50 1
71 1
36 (
0 i
93 1
: 14)
: 4)
; 12)
: e>
: 2)
: 6)
: 9)
, ID
: 3)
! 1)
1 7)
1 10)
1 5)
I 0)
1 13)
MEDIAN
INORG N
100 (
29 (
50 (
57 (
0 (
43 <
64 <
82 <
36 <
93 1
18 <
.7 1
71 i
18 i
82 <
: 14)
! 4)
: 7)
: a)
: o)
: 6>
[ 9)
t ID
[ 5)
I 13)
! 2)
t 1)
I 10)
t 2)
I 11)
500-
MEAN SEC
100 <
36 (
7 1
14 (
0 1
29 1
43 (
86 1
79 1
64 1
57 (
50 i
21 i
71 i
93 i
: 14)
: 5)
: i)
; 2)
: o)
: 4)
[ 6)
[ 12)
[ 11)
: 9)
[ 3)
[ 7)
t 3)
( 10)
( 13)
MEAN
CHLORA
93 (
43 (
100 <
71 I
50 <
21 <
29 1
0 <
14 1
7 1
86 1
64 I
79 i
36 i
57 i
: 13)
: 6)
: 14)
: 10)
; 7)
: 3)
i 4)
: o>
: 2>
i i>
[ 12)
[ 9)
[ 11)
( 5)
[ 8)
15-
MIN DO
57 <
64 (
7 <
79 <
93 (
71 (
86 (
0 (
50 <
100 1
25 1
39 1
39 i
14 i
25 i
: e)
9)
1)
: 11)
; 13)
: io>
; 12)
1 0)
I 7)
[ 14)
[ 3)
! 5)
: 5)
( 2)
: 3)
MEDIAN
DISS OftTHO P
89 (
29 <
100 <
50 (
7 (
64 (
71 1
79 1
14 1
21 1
43 I
36 (
57 i
0 i
89 i
L2)
4)
: 14)
; 7)
: i)
: 9)
: 10)
; ID
[ 2)
[ 3)
[ 6)
[ 5)
( 8)
( 0)
[ 12)
INDEX
NO
539
230
350
328
164
271
' 357
326
214
292
279
267
303
139
439

-------
    APPENDIX B





CONVERSION FACTORS

-------
                CONVERSION FACTORS




Hectares x 2.471 = acres



Kilometers x 0.6214 = miles



Meters x 3.281 = feet

                         -4
Cubic meters x 8.107 x 10   = acre/feet



Square kilometers x 0.3861 = square miles



Cubic meters/sec x 35.315 = cubic feet/sec



Centimeters x 0.3937 = inches

  •

Kilograms x 2.205 = pounds



Kilograms/square kilometer x 5.711 = Ibs/square mile

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

-------
                                   TRIBUTARY FLOW  INFORMATION  FOR  KANSAS
                                                                                           1.2/0376
LA
-------
                                   TRIBUTARY FLOW INFORMATION FOR KANSAS
                                                                                          12/0376
LAKE CODE 2011
PERRY
     MEAN MONTHLY FLOWS AND GAILY FLOWS(CMS)
TRIBUTARY   MONTh   YEAR
2011B1
2011C1
2011E2
2011ZZ
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
6
7
8
9
10
11
12
1
2
3
i»
5
6
7
8
9
74
7*.
74
75
75
75
75
75
75
75
75
75
74
74
74
75
75
75
75
75
75
75
75
75
74
74
74
75
75
75
75
75
75
75
75
75
74
74
74
75
75
75
75
75
75
75
75
75
         MEAN FLOW  DAY
0.037
0.054
0.065
0.108
0.368
0.396
0.680
0.991
2.407
0.096
0.022
0.059
0.005
0.007
0.010
0.016
0.048
0.068
0.088
0.142
0.272
0.014
0.003
0.006
0.012
0.016
0.020
0.034
0.108
0.142
0.193
0.311
0.680
0.031
0.007
0.016
0.283
0.510
0.481
0.793
2.549
2.350
5.097
7.646
21.238
0.708
0.311
0.595
12
9
14
13
6
9
13
11
7
13
10
7
12
9
It
11
8
9
13
11
7
13
10
7
12
9
14
11
8
8
11
11
7
13
10
7












FLOW  DAY
                                                  FLOW  DAY
                                                                                       FLOW
0.651
0.481
0.340
0.566
0.510
0.368
0.510
0.340
0.255
0.042
0.003
0.085
0.042
0.071
0.048
0.057
0.057
0.0
0.071
0.042
0.011
0.006
0.0
0.0
0.008
0.014
0.014
0.014
0.028
0.017
0.076
0.065
0.062
0.008
0.001
O.OC1







24
21
27









24
21
27









24
21
27


                                                                    0.991
                                                                    0.566
                                                                    0.014
                                                                    0.074
                                                                    0.068
                                                                    0.003
                                                                    0.025
                                                                    0.057
                                                                    0.008

-------
        APPENDIX D





PHYSICAL and CHEMICAL DATA

-------
STORE! RETRIEVAL DATE 76/05/03
                                                                  201101
                                                                 39 06 52.0 095 25 40.0 3
                                                                 PERRY RESERVOIR
                                                                 20087   KANSAS
                                                                                          091191
                                                                 11EPALES             2111202
                                                                  0050  FEET  DEPTH  CLASS 00
DATE
FROM
TO
74/04/12


74/06/25



74/10/02




00010
TIME DEPTH WATER
OF TEMP
DAY FEET CENT
10 00
10 00
10 00
10 00
10 00
15 40
15 40
15 40
15 40
15 40
15 40
12 00
12 00
12 00
12 00
12 00
0000
0005
0015
0030
0040
0000
0005
0015
0030
0040
0050
0000
0005
0020
0035
0050
10.0
10.0
10.0
10.0
10.0
26.7
26.8
23.3
23.0
20.6
19.9
17.6
17.6
17.5
17.5
17.5
00300 00077 00094
DO TRANSP CNDUCTVY
SECCHI FIELD
MG/L INCHES MICROMHO

10.0
10.0
10.4
10.0
14.2
6.0
7.2
6.4
2.8
2.2
8.0
8.0
8.2
8.2
8.0
32


24 422
423
399
396
379
371
26 333
337
335
333
335
00400 00410
PH T ALK
CAC03
SU MG/L
8.40
8.40
8.35
8. 35
8.30
8.70
8.60
8.30
8.20
7.90
7.90
8.09
8.13
8.11
8.11
8.09
168
171
168
168
167
160
160
160
161
162
163
164
163
164
162
163
00610 00625 00630 00671
NH3-N TOT KJEL N02&N03 PHOS-DIS
TOTAL N N-TOTAL ORTHO
MG/L MG/L MG/L MG/L P
0.070
0.080
0.070
0.080
0.080
0.040
0.050
0.060
0.050
0.050
0.040
0.030
0.030
0.040
0.020
0.020
0.500
0.500
0.400
0.500
0.400
0.600
0.400
0.400
0.400
0.400
0.400
0.400
0.200
0.200K
0.200K
0.300
1.130
1.140
1.140
1.140
1.130
1.180
1. 170
1. 140
1.030
1.250
1.210
0.870
0.880
0.870
0.860
0.860
0.031
0.035
0.034
0.034
0.035
0.015
0. 0?1
. V C. I
0.021
O.OP?
. w a c.
0.036
0.018
0.018
0.017
0.017
0.017

DATE
FROM
TO
74/04/12




74/06/25





74/10/02





TIME DEPTH
OF
DAY FEET
10 00 0000
10 00 0005
10 00 0015
10 00 0030
10 00 0040
15 40 0000
15 40 0005
15 40 0015
15 40 0030
15 40 0040
15 40 0050
12 00 0000
12 00 0005
12 00 0020
12 00 0035
12 00 0050
00665
PHOS-TOT

MG/L P
0.059
0.057
0.061
0.056
0.056
0.032
0.036
0.032
0.035
0.086
0.042
0.038
0.038
0.038
0.035
0.098
32217 00031
CHLRPHYL INCDT LT
A REMNING
UG/L PERCENT
5.1




4.3





3.0
1.0



          K VALUE KNOWN TO BE
          LESS THAN INDICATED

-------
STORET RETRIEVAL DATE 76/05/03
                                                                   201102
                                                                  39  08  37.0  095  24  12.0  3
                                                                  PERRY  RESERVOIR
                                                                  20037   KANSAS
                                                                                           091191
DATE
FROM
TO
74/04/12



74/06/26



74/10/02




DATE
FROM
TO
74/04/12



74/06/26




74/10/02



TIME DEPTH
OF
DAY FEET
12 15 0000
12 15 0005
12 15 0015
12 15 0030
10 05 0000
10 05 0005
10 05 0015
10 05 0027
11 35 0000
11 35 0005
11 35 0015
11 35 0028

TIME DEPTH
OF
DAY FEET
12 15 0000
12 15 0005
12 15 0015
12 15 0030
10 05 0000
10 05 0005
10 05 0006
10 05 0015
10 05 0027
11 35 0000
11 35 0005
11 35 0015
11 35 0028
00010
WATER
TEMP
CENT
11.0
11.0
10.9
10.8
23.4
23.2
23.0
22.0
17.2
17.2
17.2
17.2
00665
PHOS-TOT

MG/L P
0.063
0.059
0.063
0.064
0.059
0.043

0.053
0.092
0.048
0.049
0.046
0.062
11EPALES 2111202
0035 FEET DEPTH CLASS 00
00300 00077 00094 00400 00410 00610 00625 00630 00671
DO TRANSP CNDUCTVY PH T ALK NH3-N TOT KJEL N02&N03 PHOS-DIS
SECCHI FIELD CAC03 TOTAL N N-TOTAL OWTHO
MG/L

9.
10.
10.
6.
6.
6.
1.
8.
8.
8.
7.
32217
INCHES MICROMHO SU
25
8
0
0
8 24
8
4
6
2 18
4
0
8
00031
8.
8.
8.
8.
399 8.
398 8.
398 8.
399 7.
331 8.
329 8.
331 8.
333 8.

40
35
30
30
40
30
20
90
09
13
13
11

MG/L
172
173
170
170
165
167
164
171
164
163
164
164

MG/L
0.050
0.040
0.040
0.060
0.090
0.070
0.090
0.090
0.030
0.020
0.030
0.040

MG/L
0.600
0.500
0.600
0.600
0.600
0.400
0.400
0.400
0.400
0.500
0.500
0.500

MG/L
0.780
0.760
0.780
0.880
1.000
0.850
1.030
1.200
0.800
0.810
0.820
0.820

MG/L P
0.018
0.017
0.018
0.022
0.011
0.012
0.016
0.017
0.015
0.015
0.016
0.016

CHLRPHYL INCDT LT
A
UG/L
13.



4.




5.



REMNING
PERCENT
2



9

1.0


2













































































































-------
STORET RETRIEVAL DATE 76/05/03
                                                                  201103
                                                                 39 09 53.0 095 27 33.0 3
                                                                 PERRY RESERVOIR
                                                                 20087   KANSAS
                                                                                          091191
DATE
FROM
TO
74/04/12




74/06/26




74/ 10/02





DATE
FROM
TO
74/04/12




74/06/26





74/10/02




TIME DEPTH
OF
DAY FEET
12 40 0000
12 40 0005
12 40 0015
12 40 0030
12 40 0045
10 30 0000
10 30 0005
10 30 0015
10 30 0030
10 30 0044
10 25 0000
10 25 0005
10 25 0015
10 25 0030
10 ?5 0044

TIME DEPTH
OF
DAY FEET
12 40 0000
12 40 0005
12 40 0015
12 40 0030
12 40 0045
10 30 0000
10 30 0005
10 30 0006
10 30 0015
10 30 0030
10 30 0044
10 25 0000
10 25 0005
10 25 0015
10 25 0030
10 25 0044
00010
WATER
TEMP
CENT
10.7
10.5
10.5
10.5
10.5
23.5
23. S
23.0
22.2
21.0
17.3
17.3
17.3
17.3
17.3
00665
PHOS-TOT

MG/L P
0.049
0.045
0.048
0.048
9.043
0.079
0.05S

0.049
0.080
0.095
0.044
0.044
0.055
0.055
0.067
00300 00077
DO TRANSP

MG/L

10.
10.
10.
10.
2.
S.
5.
3.
2.
8.
9.
B.
8.
8.
32217
SECCHI
INCHES
24
0
0
2
2
0 12
4
4
8
4
4 18
0
4
4
4
00031
00094
CNDUCTVY
FIELD
MICROMHO





392
393
395
394
387
327
335
335
333
331

11EPALES 2111202
0050 FEET DEPTH CLASS 00
00400 00410 00610 00625
PH T ALK NH3-N TOT KJEL

SU
8.40
8.40
8.35
8.35
8.35
8.30
8.20
8.10
8.00
8.00
8.09
8.19
8.19
8.07
8.11

CAC03
MG/L
174
174
175
174
174
160
159
164
166
170
169
168
166
165
166

TOTAL
MG/L
0.080
0.090
0.070
0.070
0.070
0.050
0.080
0.050
0.080
0.070
0.030
0.040
0.030
0.030
0.020

N
MG/L
0.700
0.500
0.500
0.600
0.600
0.400
0.400
0.300
0.300
0.400
0.600
0.400
0.500
0.400
0.400

00630
N02&N03
N-TOTAL
MG/L
0.920
0.920
0.910
0.910
0.900
1.900
1.950
1.510
1.630
1.640
0.790
0.800
0.800
0.800
0.780

00671
PHOS-DIS
ORTHO
MG/L P
0.016
0.016
0.016
0.016
0.021
0.029
0.027
0.022
0.022
0.021
0.015
0.016
0.016
0.016
0.020

CHLRPHYL INCOT LT
A
UG/L
9.




1.





6.




REMNING
PERCENT
6




5

1.0



2



































































































































-------
STORET RETRIEVAL DATE 76/05/03
                                                                  201104
                                                                 39 13 43.0 095 27 23.0 3
                                                                 PERRY RESERVOIR
                                                                 20037   KANSAS
                                                                                          091191
UEPALES 2111202 .
0035 FEET DEPTH CLASS 00
DATE
FROM
TO
74/04/12


74/06/26

74/10/04



DATE
FROM
TO
74/04/12



74/06/26




74/10/04




TIME
OF
DAY
13 15
13 15
13 15
13 15
11 00
11 00
11 00
11 00
09 55
09 55
09 55
09 55

TIME
OF
DAY
13 15
13 15
13 15
13 15
11 00
11 00
11 00
11 00
11 00
09 55
09 55
09 55
09 55
09 55
DEPTH
FEET
0000
0005
0015
0030
0000
0005
0015
0027
0000
0005
0015
0028

DEPTH

FEET
0000
0005
0015
0030
0000
0003
0005
0015
0027
0000
0003
0005
0015
0026
00010
WATER
TEMP
CENT
11.7
11.7
11.6
11.5
23.5
23.4
23.3
22.2
16.3
16.2
16.1
15.9
00665
PHOS-TOT

MG/L P
0.037
0.045
0.049
0.057
0.121

0.117
0.133
0.116
0.052

0.052
0.059
0.064
00300 00077 00094 00400 00410
00 TRANSP CNOUCTVY PH T ALK
SECCH1 FIELD CAC03
MG/L INCHES MICROMHO SU MG/L
20
9.4
9.2
9.2
5.4 12
5.0
4.8
3.2
8.4 18
8.6
8.8
8.4
32217 00031
CHLRPHYL INCDT LT
A REMNING
UG/L PERCENT
7.1



0.9
1.0



12.8
1.0



8
8
8
8
376 8
376 8
382 8
393 8
167 7
267 8
279 7
279 7


















.30
.30
.30
.30
.20
.10
.00
.00
.75
.05
.99
.91


















204
202
203
201
142
148
147
159
167
168
170
172


















00610 00625 00630 00671
NH3-N TOT KJEL N02&N03 PHOS-DIS
TOTAL N N-TOTAL ORTHO
MG/L MG/L MG/L MG/L P
0.130
0.130
0.130
0.130
0.090
0.130
0.080
0.080
0.050
Oe040
Oo060
0.060


















0.800
0.600
0.700
0.700
0.400
0.500
0.500
0.400
0.900
0.600
0.600
0.500


















0.460
0.460
0.450
0.480
1.960
1.940
1.800
1.560
0.630
0.580
0.560
0.540


















0.010
0.009
0.008
0.009
0.051
0.050
0.043
0.029
0.015
0.012
0.011
0.011



















-------
STORET RETRIEVAL DATE 76/05/03
                                                                  301105
                                                                 39 09 00.0 095 28 53.0 3
                                                                 PERRY RESERVOIR
                                                                 20      KANSAS
                                                                                          091191
11EPALES
2111202
0033 FEET DEPTH CLASS

DATE
FROM
TO
74/06/36



74/10/02




DATE
FROM
TO
74/06/36



74/10/02






TIME DEPTH
OF
DAY FEET
09 40 0000
09 40 0005
09 40 0015
09 40 0037
11 00 0000
11 00 0005
11 00 0015
11 00 0024

TIME DEPTH
OF
DAY FEET
09 40 0000
09 40 0005
09 40 0015
09 40 0027
11 00 0000
11 00 0001
11 00 0004
11 00 0005
11 00 0015
11 00 0024
00010
HATER
TEMP
CENT
24.4
24.3
23.8
22.6
16.9
16.9
16.8
16.5
00665
PHOS-TOT

MG/L P
0.064
0.053
0.079
0.149
0.047


0.050
0.047
0.058
00300
DO

MG/L
7.2
6.8
5.4
2.0
8.8
8.4
8.2
8.2
32217
CHLRPHYL
A
UG/L
2.9



1.9





00077
TRANSP
SECCHI
INCHES
24



23



00031
INCDT LT
REMNING
PERCENT

1.0



50.0
1.0



00094
CNDUCTVY
FIELD
MICROMHO
407
406
404
402
329
329
331
331














00400
PH

SU
8.60
8.40
8.10
7.90
8.13
8.17
8.17
8.15














00410
T ALK
CAC03
MG/L
161
161
162
167
167
162
164
164














00610
NH3-N
TOTAL
MG/L
0.060
0.060
0.120
0.190
0.020
0.030
0.030
0.030














00
00625
TOT KJEL
N
MG/L
0.800
0.400
0.500
0.500
0.600
0.300
0.300
0.500















00630
N02&N03
N-TOTAL
MG/L
1.380
1.260
1.100
0.870
0.770
0.760
0.750
0.740















00671
PHOS-DIS
ORTHO
MG/L P
0.039
0.024
0.024
0.017
0.014
0.013
0.013
0.012















-------
       APPENDIX E

TRIBUTARY AND WASTEWATER
  TREATMENT PLANT DATA

-------
STORE! RETRIEVAL DATE 76/05/0*
  DATE   TIME DEPTH N02S.N03
  FROM    OF
   TO    DAY  FEET
74/10/12
74/11/09
74/12/14
75/01/12
75/02/OB
75/03/09
75/04/13
75/05/11
75/05/24
75/06/07
75/06/21
75/07/13
75/07/27
75/08/10
75/09/07
13 15
14 10
13 50
11 45
13 20
08 45
11 45
12 50
15 20
14 10
13 10
13 00
14 45
13 25
13 00
                                                                   2011A1
                                                                 39  36  35.0 095  25  17.0  4
                                                                 DELAWARE RIVER
                                                                 20 .     7.5 P.ERRY
                                                                 G/PERRY RESERVOIR         091191
                                                                 dANK SAMPLE .5  Ml  3ELOW PERRY  DAM
                                                                 11EPALES              2111204
                                                                   0000  FEET  DEPTH   CLASS  00
'0630
IS.N03
OTAL
IG/L
0.840
0.760
0.624
0.552
0.490
0.472
0.460
0.345
0.345
0.330
0.840
0.760
0.270
0.085
0.600
00625
TOT KJEL
N
MG/L
0.800
0.700
0.600
0.500
0.300
1.000
1.0?5
0.850
1.000
0.550
0.500
0.550
1.250
1.250
0.650
00610
NH3-N
TOTAL
MG/L
0.025
0.035
0.008K
0.072
C.016
0.040
0.050
0.055
0.105
0.020
0.027
0.080
0.340
0.320
0.040
00671
PriOS-DIS
ORTHO
MG/L P
0.020
0.020
0.010
0.030
0.008K
0.008K
0.005
0.005
0.015
0.005
0.025
0.030
0.020
0.040
0.030
00665
PH05-TOT

MG/L P
0.045
0.020
0.030
0.042
0.020
0.020
0.035
0.040
0.080:
0.0 40;
0.080
0.110
0.120.
0.165
0.090
   K VALUE KNOrfN TO BE
   LESS THAN INDICATED

-------
STORET RETRIEVAL DATE 76/05/04
  DATE   TIME DEPTH N02&N03
  FROM    OF
   TO    DAY  FEET
74/11/09
75/01/11
75/02/08
75/03/08
75/04/12
75/05/11
75/05/24
75/06/07
75/06/21
75/07/13
75/07/27
75/08/10
75/09/07
15 05
09 35
10 55
09 40
09 55
09 40
09 30
09 55
10 ?5
10 15
08 15
07 30
09 20
09 ?5
                                                                  2011A2
                                                                 39 20 25.0 095 26 bO.O 4
                                                                 DELAWARE RIVER
                                                                 20      7.5 VALLEY FALLS
                                                                 T/PEnRY RESERVOIR        091191
                                                                 ST RT 16 3RDG .5 MI E OF VALLEY FALLS
                                                                 11EPALES             2111204
                                                                  0000 FEET  DEPTH  CLASS 00
0630
!i.N03
OTAL
10/L
0.400
0.341
0.480
0.400
1.000
0.300
0.125
0.095
1.200
1.450
0.005
0.010
0.005
0.300
00625
TOT KJEL
N
MG/L
1.100
1.50C
1.100
2.100
1.350
0.600
1.050
1.050
0.800
0.950
0.450
0.450
0.800
0.850
00610
NH3-N
TOTAL
MG/L
0.047
0.030
0.064
0.232
0.124
0.030
0.050
0.025
0.025
0.035
0.020
0.020
0.045
0.015
00671
PHOS-OIS
ORTHO
MG/L P
0.125
0.110
0.205
0.104
0.116
0.090
0.060
0.040
0.103
0.105
0.070
0.080
0.060
0.070
00665
PHOS-TOT

MG/L P
0.150
0.140
0.220
0.320
0.180
0.140
0.140
0.120
0.320
0.320
0.140
0.110
0.140
0.200

-------
STORE! RETRIEVAL DATE 76/05/04
                                                                  2011A3
                                                                 39 22 20.0 095 28 45.0 4
                                                                 DELAWARE RIVER
                                                                 20      7.5 VALLEY FALLS
                                                                 T>PE*RY RESERVOIR
                                                                 BROG ON N-S RO 1 M W
                                                                  0000 FEET  DEPTH
      091191
    2 M N VLY FALLS
  2111204
CLASS 00
DATE
FROM
TO
74/10/12
74/11/09
74/ 12/14
75/01/11
75/02/08
75/03/08
75/04/12
75/05/11
75/05/24
75/06/07
75/06/21
75/07/13
75/07/27
75/08/10
75/09/07
00630 00625
TIME DEPTH N02&N03 TOT KJEL
OF N-TOTAL N
DAY FEET
10
10
10
11
10
10
10
10
10
10
10
08
08
09
10
10
00
05
20
05
30
05
00
30
50
30
50
00
50
05
MG/L
0
0
0
0
1
1
0
0
0
1
1
0
0
0
0
.168
.352
.352
.800
.800
.155
.155
.450
.540
.250
.400
.125
.090
.045
.260
MG/L
1.
0.
0.
1.
1.
1.
0.
1.
1.
1.
1.
0.
0.
0.
1.
400
800
900
500
600
350
850
500
500
450
950
300
550
550
050
00610 00671 00665
NH3-N PHOS-DIS PhOS-TOT
TOTAL ORTHO
MG/L
G.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
465
240
025
096
480
234
020
015
030
050
015
010
020
030
015
MG/L
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
p
143
160
110
130
176
144
130
115
150
150
140
110
130
055
145
MG/L P
0.360
0.190
0.140
0.160
0.270
0.280
0.230
0.480
0.380
0.400
0.720
0.160
0.230
0.220
0.380

-------
STORET RETRIEVAL DATE 76/05/04
                                                                  2011^1
                                                                 39  11 40.0 095  23  32.0  4
                                                                 SLOUGH CREEK
                                                                 20       7.5 OZA*KIE
                                                                 T/PEKRY  RESERVOIR         091191
                                                                 dRDG 5.4 M SE OF OLD  T«(N  PUBLIC  USE  AREA
                                                                 11EPALES             2111204
                                                                  0000 FEET  DEPTH  CLASS  00
DATE
FROM
TO
74/10/12
74/11/09
74/12/14
75/01/13
75/02/08
75/03/09
75/04/13
75/05/11
75/05/24
75/06/07
75/06/21
75/07/13
75/07/27
75/08/10
75/09/07
00630 00625
TIME DEPTH N02&N03 TOT KJEL
OF N-TOTAL N
DAY FEET
12
12
13
13
12
09
11
12
14
13
12
12
11
12
12
45
50
15
50
55
20
00
25
25
40
45
20
00
55
35
MG/L
0.
0.
0.
0.
0.
0.
0.
0.
1.
0.
0.
0.
0.
0.
0.
264
750
312
920
270
528
135
460
400
400
345
200
010
005
620
MG/L
2
0
0
0
0
0
0
1
1
0
0
0
1
1
1
.000
.300
.300
.700
.700
.700
.450
.550
.450
.525
.600
.450
.050
.100
.750
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
0
.050
.040
.030
.072
.064
.040
.015
.015
.075
.025
.010
.055
.010
.020
.165
MG/L P
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
.075
.060
.025
.104
.032
.040
.010
.035
.050
.010
.040
.005
.015
.015
.045
MG/L P

0.070
0.045
0.104
0.050
0.060
0.050
0.230
0.200
0.095
0.120
0.060
0.140
0.150
0.33C

-------
STORE! RETRIEVAL DATE 76/05/04
  DATE   TIME DEPTH N02&N03
  FROM    OF
   TO    DAY  FEET
74/10/12
7^/11/09
74/12/14
75/01/11
75/02/08
75/04/13
75/05/11
75/05/24
75/06/07
75/06/21
75/07/13
75/07/27
75/08/10
75/09/07
12 15
11 30
12 20
13 15
12 05
10 35
11 25
12 40
13 25
12 30
11 50
10 45
12 40
12 15
                                                                  20 1 i C1
                                                                 39  13 20.0 095 25  15.0 4
                                                                 LITTLE SLOUGH CREE*
                                                                 20      7.5 pZAWtSJE
                                                                 T/PErtRr RESERVOIR         091191
                                                                 SEC  *D BROG .8 Ml  S OF ST RT  92  JCT
                                                                 IIE^ALES             2111204
                                                                  0000 FEET  DEPTH  CLASS  00
0630
&N03
OTAL
iG/L
0.336
0.760
0.288
1.240
0.720
0.110
0.230
4.000
0.330
0.375
0.135
0.085
0.005
0.440
00625
TOT KJEL
N
MG/L
3.100
0.4QO
0.300
1.600
0.800
0.750
0.700
2.900
0.800
1.100
0.550
1.450
1.800
1.550
00610
NH3-N
TOTAL
MG/L
0.470
0.035
0.015
0.048
0.024
0.030
0.020
0.340
0.015
0.005
0.030
0.150
0.020
0.123
00671
PriOS-OIS
ORTHO
MG/L P
0.100
0.035
0.010
0.035
0.016
0.007
0.015
0.070
0.005K
0.015
0.010
0.020
0.020
0.020
00665
PHOS-TOT

MG/L P
0.780
0.050
0.020
0.160
0.020
0.010
0.090
0.230
0.070
0.140
0.050
0.170
0.230
0.270
  K VALUE KNOWN TO BE
  LESS THAN INDICATED

-------
STORE! RETRIEVAL DATE 76/05/04
  DATE   TIME DEPTH N02&N03
  FROM    Of
   TO    DAY  FEET
74/10/13
74/11/09
74/12/14
75/01/11
75/02/08
75/03/08
75/04/13
75/05/11
75/05/24
75/06/07
75/06/21
75/07/13
75/07/27
75/09/07
10 58
10 45
11 15
12 30
11 00
12 00
11 05
10 50
11 55
11 55
11 20
09 50
08 55
11 00
                                                                  2011D1
                                                                 39 21 00.0 095 25 21.0 4
                                                                 BRUSi CREEK
                                                                 20      7.5 VALLEY FALLS
                                                                 T/PERRY RESERVOIR        0911*1
                                                                 BROG 2.7 MI HE OF VALLEY FALLS
                                                                 11EPALES             2111204
                                                                  0000 FEET  DEPTH  CLASS 00
0630
'&N03
OTAL
IG/L
0.024
0.650
0.750
2.640
3.800
1.055
0.300
0.290
0.390
0.620
0.530
0.020
0.015
0.015
00625
TOT KJEL
N
MG/L
0.850
1.100
0.600
1.300
0.500
0.650
1.150
0.700
0.950
0.700
0.450
0.350
0.450
1.225
00610
NH3-N
TOTAL
MG/L
0.075
0.040
0.025
0.040
0.208
0.040
0.025
0.020
0.030
0.030
0.025
0.025
0.035
0.030
00671
PHOS-DIS
ORTHO
MG/L P
0.035
0.035
0.015
0.035
0.032
0.016
0.005K
0.010
0.015
0.015
0.045
0.010
0.025
0.025
00665
PHOS-TOT

MG/L P
0.085
0.035
0.030
0.190
0.070
0.030
0.010K
0.070
0.045
0.050
0.085
0.040
0.070
0.185
 K VALUE KNOWN TO BE
 LESS THAN INDICATED

-------
STORET RETRIEVAL DATE 76/05/04
  DATE   TIME DEPTH N02&N03
  FROM    OF
   TO    DAY  FEET
74/10/12
74/11/09
74/12/14
75/01/11
75/02/08
75/03/08
75/04/13
75/05/11
75/05/24
75/06/07
75/06/21
75/07/13
75/07/27
75/08/10
75/09/07
09 15
09 05
09 00
10 20
09 15
09 25
09 10
09 05
09 25
09 55
16 30
07 15
06 30
08 45
09 10
                                                                  2011E1
                                                                 39 11 30.0 095 33 05.0 4
                                                                 ROCK CREEK
                                                                 20      7.5 HER I DEN
                                                                 T/PE«RY RESERVOIR-        091191
                                                                 SEC 30 dROG 1 MI E OF MERIDEN
                                                                 11EPALES             2111204
                                                                  0000 FEET  DEPTH  CLASS 00
0630
&N03
OTAL
G/L
0.144
1.360
0.780
1.400
1.300
0.90S
0.260
0.660
0.860
1.050
1.300
0.710
0.320
1.000
0.690
00625
TOT KJEL
N
MG/L
.4.400
1.500
0.200
1.300
0.700
0.750
0.475
1.030
1.100
1.000
0.800
0.800
1.150
3.300
1.450
00610
NH3-N
TOTAL
MG/L
0.903
0.400
0.020
0.072
0.056
0.028
0.025
0.035
0.090
0.040
0.020
0.040
0.210
0.280
0.175
00671
PHOS-DIS
URTHO
MG/L P
0.025
0.025
0.005
0.035
0.016
0.008
0.010
0.020
C.025
0.030
0.035
0.005K
0.010
0.030
0.040
00665
PHOS-TOT

MG/L P

0.040
0.020
0.220
0.030
0.030
0.020
0.215
0.090
0.120
0.130
0.040
0.130
0.260
0.220
 K VALUE KNOWN TO 8E
 LESS THAN INDICATED

-------
STORE! RETRIEVAL DATE 76/05/04
                                                                  2011E2
                                                                 39 12 32.0 095 34  10.0 4
                                                                 rtOCK CREEK
                                                                 20      7.5 MERIDEN
                                                                 T/PE?RY RESERVOIR        091191
                                                                 BRDG ON LGriT OTY «G  1 MI N OF MERIDEN
                                                                 11EPALES             2111204
                                                                  0000 FEET  DEPTH  CLASS 00
DATE
FROM
TO
74/10/12
74/11/09
74/12/14
75/01/11
75/02/08
75/03/08
75/04/12
75/05/11
75/05/24
75/06/07
75/06/21
75/07/13
75/08/10
75/09/07
00630 00625
TIME DEPTH N02&N03 TOT KJEL
OF M-TOTAL N
DAY FEET
09
14
08
10
08
09
08
08
09
09
09
07
08
08
35
40
45
00
35
05
55
45
00
40
45
35
30
45
MG/L
0
0
0
2
0
0
0
0
1
0
0
0
1
1
.416
.400
.288
.800
.290
.605
.020
.500
.000
.510
.630
.980
.050
.150
MG/L
1.
0.
0.
1.
0.
0.
0.
1.
1.
0.
0.
0.
0.
1.
900
700
700
600
600
400
600
200
850
800
450
500
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.
055
050
015
056
040
016
020
080
123
025
015
040
055
075
MG/L
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
P
045
050
005
030
016
012
015
015
025
025
025
015
015
055
MG/L P
0.470
0.140
0.040
0.170
0.040
0.040
0.020
0.180
0.120
0.120
0.070
0.030
0.050
0.230

-------
STORE! RETRIEVAL DATE 76/05/04
  DATE   TIME DEPTH N02&N03
  FROM    OF
   TO    DAY  FEET
74/10/12
74/11/09
74/12/14
75/01/12
75/02/08
75/03/09
75/04/13
75/05/11
75/05/24
75/06/07
75/06/21
75/07/13
75/08/10
75/09/07
13 00
13 05
13 30
12 20
13 05
09 10
11 25
12 40
14 50
13 50
12 55
12 40
13 10
12 45
                                                                  2011F1
                                                                 39 09 55.0 095 23 07.0 4
                                                                 EVANS CREEK
                                                                 20      7.5 OZAWKlt
                                                                 T/PE-fRY RESERVOIR        091191
                                                                 BRDG 6.5 MI S« OF OSKALOOSA
                                                                 11EPALES             2111204
                                                                  0000 FEET  DEPTH  CLASS 00
0630
'&N03
OTAL
IG/L
0.810
0.448
0.152
0.368
0.208
0.160
0.015
0.015
0.200
0.130
0.210
0.155
0.010
0.060
00625
TOT KJEL
N
MG/L
2.400
0.500
0.200
1.200
0.300
1.100
0.250
0.050K
0.800
0.350
0.400
0.400
0.200
0.350
00610
NH3-N
TOTAL
MG/L
0.030
0.030
0.017
0.032
0.056
0.024
0.020
0.010
0.025
0.025
0.015
0.025
0.025
0.035
00671
PHOS-OIS
ORTHO
MG/L P
0.185
0.030
0.015
0.032
0.008K
0.008K
0.005K
0.005K
0.010
0.005K
0.010
0.020
0.005
0.010
00665
PHOS-TOT

MG/L P
0.440
0.030
0.015
0.032
0.010K
0.010
0.020
0.010*
0.050
0.030
0.060
0.100
0.040
0.080
  K  VALUE  KNOWN TO BE
  LESS  THAN  INDICATED

-------
STORET RETRIEVAL DATE 76/05/04
  DATE   TIME DEPTH N028.N03
  FROM    OF
   TO    DAY  FEET
74/10/12
7<*/ll/09
74/12/14
75/01/11
75/02/08
75/03/08
75/04/12
75/05/11
75/05/24
75/06/07
75/06/21
75/07/13
75/07/27
75/09/07
11
11
11
12
11
12
11
11
12
12
11
10
09
11
45
05
35
50
20
25
30
10
15
20
35
15
10
15
                                                                   2011G1
                                                                  39 16  12.0  095  23  15.0  4
                                                                  FISHPOND  CREEK
                                                                  20     7.5 VALLEY  FALLS
                                                                  T/PEKRY RESERVOIR         091191
                                                                  riRDG  7.2  MI N   OF  OSKALOOSA
                                                                  11EPALES              2111204
                                                                   0000  FEET   DEPTH   CLASS  00
0630
'J.N03
OTAL
G/L
0.352
1.000
0.750
1.560
4.300
0.830
0.315
0.560
4.730
1.050
0.660
0.230
0.025
0.590
00625
TOT KJEL
N
MG/L
3.700
0.400
0.400
2.300
0.400
0.600
1.250
0.550
1.950
0.600
0.400
0.350
0.650
1.000
00610
NH3-N
TOTAL
MG/L
0.600
0.030
0.015
0.032
0.072
0.016
0.025
0.035
0.195
0.020
0.010
0.020
0.035
0.030
00671
PHOS-OIS
ORTHO
MG/L P
0.420
0.035
0.010
0.050
0.016
0.008
0.005
0.005
0.060
0.010
0.015
0.005
0.010
0.075
00665
PHOS-TOT

MG/L P
0.670
0.035
0.020
0.440
0.030
0.020
0.050
0.030
0.210
0.040
0.040
0.040
0.090
0.230

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STORE! RETRIEVAL DATE 76/05/04
                                                                  2011AA          TF2011AA     P002386
                                                                 39 39 00.0 095 32 OOoO 4
                                                                 NORTON
                                                                 20      7.5 NORTON
                                                                 T/P£RRY RES.             091192
                                                                 DELAWARE RIVER
                                                                 11EPALES             2141204
                                                                  0000 FEET  DEPTH  CLASS 00
OOfclO
DATE
FROM
TO
75/02/24
75/03/31
75/04/23
75/05/14
75/06/06
75/06/26
75/07/16
75/08/06
75/08/26
75/09/17
75/10/08
75/10/31
75/12/23
00625
TIME DEPTN N02&N03 TOT KJEL
OF N-TOTAL N
DAY FEET MG/L MG/L
14
08
07
10
08
10
10
11
11
11
10
14
11
00
00
45
00
30
00
00
00
00
00
30
00
00
4.640
5.400
4.700
17.300
10.500
7.900
10.500
13.500
5.100
5.600
5.600
14.700
10.500
28.000
12.000
5.200
9.700
3.700
4.600
3.750
14.000
12.500
15.500
11.000
15.000
14.500
00610
00671
00665
50051
50053
NH3-N PHOS-DIS PHOS-TOT FLOW CONOUIT
TOTAL ORTNO RATE FLOW-MGO
MG/L MG/L P MG/L P INST MGD MONTNLY
0.230
0.110
0.240
0.160
o.iao
0.460
0.580
0.350
0.620
0.087
0.175
0.140
5.000
5.700
6.000
9.200
5.500
5»200
7.500
8.800
7.700
8.200
10.500
9.400
8.100
8.900
6.700
6.200
9.700
7.200
5.500
7.500
9.400
12.500
9.500
12.000
17.500
9.850
0
0
0
0
0
0
0
0
0
0
0
0
.598
.320
.684
.604
.720
.568
.688
.744
.745
.608
.568
.598
Oo540
Oo365
Oo605
Oo598
Oo698
0 = 5^8
Oo598
Oo6<»5
Oo686
Oo568
0»588
0»554

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STORE! RETRIEVAL DATE 76/05/04
                                                                  20U*A          TF2011WA     P003369
                                                                  39 26 20.0 095 43 30.0 4
                                                                  HOLTON
                                                                  20      7.5 HOLTON
                                                                  T/PERRY RES.             091191
                                                                  ELKS CREEK
                                                                  11E?ALES             2141204
                                                                  0000 FEET  DEPTH  CLASS 00
DATE
FROM
TO
75/02/10
75/03/10
75/04/10
75/05/01
75/05/22
75/06/13
75/07/03
75/07/24
75/08/15
75/09/0*
75/09/25
75/10/17
75/11/06
00630
TIME DEPTH N02&N03
OF N-TOTAL
DAY FEET
09
09
09
09
09
09
09
09
09
09
09
09
09
00
00
00
00
00
00
00
00
00
00
00
00
00
MG/L
7
4
0
1
1
8
3
0
12
4
4
11
7
.0*0
.640
.880
.300
.100
.300
.800
.250
.000
.100
.100
.500
.800
00625
TOT KJEL
N
MG/L
7.000
11.000
13.500
12.300
39.000
4.100
10.050
12.000
9.700
4.200
19.500
17.000
17.000
00610 00671
NH3-N PHOS-DIS
TOTAL ORTHO
MG/L
4.000
8.300
0.270
0.079
0.320
0.050K
O.C25K
0.260
0.550
0.650
1.570
1.720
0.210
MG/L P
9.200
9.000

8,330
6.600
1,700
7.250
11.000
16.000
11.000
13.000
13.000
13oOOO
00665
PHOS-TOT
50051 50053
FLOW CONDUIT
RATE FLOW-MOD
MG/L P INST MGD MONTHLY
9

12
12
15
2
8
12
18
12
16
13
16
.600

.500
.500
.000
.200
.500
.800
• 500
.500
.000
.000
.000
0.652
0.672
0.320
0.760
0.400
0.598
0.690
0.680
0.280
0.320
0.200
0.260

Oo660
Oo679
0.380
0.698
0.270
0.624
0.680
0.680
0.280
0.380
0.380
0.250

    K  VALUE  KNOWN  TO BE
    LESS  THAN  INDICATED

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STORE! RETPIEVAL  DATE  76/05/04
                                                                   2011YA          YF2011YA     P000415
                                                                  39 37 30.0 095 48 30oO  4
                                                                  WETMORE
                                                                  20      7.5 WETMORE
                                                                  T/PERRY RESERVOIR        091191
                                                                  SPRING CREEK
                                                                  11EPALES             2141204
                                                                   0000 FEET  DEPTH CLASS 00
DATE
FROM
TO
75/02/1*
75/03/1*
75/04/14
75/05/05
75/05/27
75/06/16
75/07/07
75/07/22
75/08/12
75/09/03
75/09/24
75/10/14
75/11/04
00630
TTME DEPTH NO2&.N03
Of N-TOTAL
DAY FEET
09

08
08
08
08
07
08
09
08
09
09
09
00

30
15
00
00
30
30
00
30
00
00
00
MG/L
6.730
2.400
3.600
4.500
5.300
7.200
7.700
7.000
10.500
10.500
10.500
6.300
8.400
00625
TOT KJEL
N
MG/L
18.000
26.500
11.500
8.500
8.900
2.600
5.700
3.000
2.800
2.900
3.900
3.300
12.000
00610 00671
NH3-N PHOS-DIS
TOTAL ORTHO
MG/L
3
7
0
0
0
0

0
0
0
0
0
0
.680
.300
.280
.050
.100
.050K

.280
.140
.050
.125
.075
.240
MG/L P
2
6
0
5
5
2
5
10
12
11
13
12

.810
.000
.250
.500
.000
.700
.900
.500
.000
.500
.300
.000

00665
PHOS-TOT
50051 50053
FLOW CONDUIT
RATE FLOW-MGO
MG/L P INST MGD MONTHLY
11.000

9.300
11.000
11.300
4.800
7.700
12.000
12.500
11.500
13.500
12.000
10.500


0.029
0.035
0.027
0.030
0.035
0.019
0.014
0.019
0.027
0.029
0.027


0.029
0.041
0.027
0.029
0.043
0.019
0.014
0.019
0.019
0.019
Oo027
    K VALUE KNOWN TO BE
    LESS THAN INDICATED

-------
STORET RETRIEVAL DATE 76/05/04
                                                                  2011ZA          PD2011ZA     P000359
                                                                 39 40 20.0 095 24 40*0 4
                                                                 EVEREST
                                                                 20      7.5 EVEREST
                                                                 T/PERRY RESERVOIR        091192
                                                                 GRASSHOPPER CREEK
HEP ALES
2141204
0000 FEET DEPTH CLASS 00

DATE
FROM
TO
75/02/24
75/03/24
75/04/24
75/05/16
75/06/06
75/07/01
75/07/18
75/08/15
75/09/06
75/09/25
75/10/20
75/11/12
75/12/02

TIME DEPTH
OF
DAY FEET
10 00
11 30

11 00
11 00
10 30
09 30
19 00
08 45
15 30
15 30
14 00
00 00
00630
N02&N03
N-TOTAL
MG/L
0.050
0.072
0.300
0.200
0.300
0.200
0.150
0.150
0.100
0.100
0.025
0.150
0.175
00625
TOT KJEL
N
MG/L
17.000
18.000
10.500
12.000
6.000
2.500
3.900
5.000
5.300
7.200
8.000
8.600
7.100
00610
NH3-N
TOTAL
MG/L
2.450
0.348
0.310

0.140
0.035
0.120
0.440
0.290
0.210
0.050
0.050
0.038
00671
PHOS-D1S
ORTHO
MG/L P
5.000
7.800
3.400
2.000
2.020
3.200
2.000
2.300
2.400
1.300
1.630
2.100
2.200
00665
PHOS-TOT

MG/L P
10.500
9.100
4.700
2.900
2.900
3.400
a. 200
2.500
2.500
1.800
2.300
3.200
3.900
50051
FLOW
RATE
INST MGD
0.033
0.033
0.033
0.033
0.033
0.033
0.033
0.033
0.033
0.033
0.033
0.033
0.038
50053
CONDUIT
FLOW-MOD
MONTHLY
0.033
0.033
0.032
0.032
0.032
0.032
0.032
0.032
0.032
0.032
0.033
0.033
0.0003

-------