U.S. ENVIRONMENTAL PROTECTION AGENCY
           NATIONAL EUTROPHICATION SURVEY
                    WORKING PAPER SERIES

                                          REPORT
                                            ON
                                      MILFORD RESERVOIR
                                   CLAY AND GEARY COUNTIES
                                          KANSAS
                                       EPA REGION VII
                                    WORKING PAPER No, 519
 CORVALLIS ENVIRONMENTAL RESEARCH LABORATORY - CORVALLIS, OREGON
                            and
ENVIRONMENTAL MONITORING & SUPPORT LABORATORY - LAS VEGAS, NEVADA
 699-440

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                                     REPORT
                                       ON
                               MILFORD RESERVOIR
                            CLAY AND GEARY COUNTIES
                                     KANSAS
                                 EPA REGION VII
                             WORKING PAPER No, 519
        WITH THE COOPERATION OF THE
KANSAS DEPARTMENT OF HEALTH AND ENVIRONMENT
                  AND THE
           KANSAS NATIONAL GUARD
                APRIL, 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                    3
III.   Lake Water Quality Summary                                 4
 IV.   Nutrient Loadings                                          9
  V.   Literature Reviewed                                       14
 VI.   Appendices                                                15

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                                 11
                          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)J, 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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                                 TM
    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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                                    IV


                      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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                                                                                            •LJ
                                                                                        Map Location
MILFORD RESERVOIR

8  Tributary Sampling Site
 X  Lake Sampling Site
9  Sewage  Treatment Facility
       Scale
                                                »r30'

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                            MILFORD  RESERVOIR
                             STORE!  NO.  2009

I.   CONCLUSIONS
    A.   Trophic Condition:
            Survey data  indicate that  Milford  Reservoir  is  eutrophic.
        It ranked thirteenth in  overall  trophic  quality  when  the  15
        Kansas reservoirs sampled in 1974  were compared  using a com-
        bination of six  lake parameters*.   Eleven  of  the reservoirs
        had less median  total  phosphorus,  11 had less and one had  the
        same median dissolved  phosphorus,  nine had less  median in-
        organic nitrogen, 12 had less  mean chlorophyll a_, and three
        had greater mean Secchi  disc transparency.  Depression of
        dissolved oxygen with  depth  occurred at  stations 1  and 3  in
        June.
            Survey limnologists  did  not  observe  macrophytes or surface
        concentrations of algae  but  noted  turbid water in June and
        October at sampling station  4.
    B.   Rate-Limiting Nutrient:
            The algal assay results  indicate that  Milford Reservoir was
        phosphorus limited  at  the time the assay sample  was collected
        (04/11/74).
            The reservoir data indicate  phosphorus limitation at all
        sampling times.
  See  Appendix  A.

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    C.  Nutrient Controllability:
            1.  Point sources—Point sources contributed 3.2% of the
        total phosphorus input to Milford Reservoir during the sampling
        year.  The City of Clyde added 0.3% of the total; Concordia,
        1.2%; Morganville, <0.1%; Wakefield, 0.2%; Clay Center, 1.3%;
        and Clifton, 0.2%.
            The present phosphorus loading of 6.79 g/m 2/yr is nearly
        eleven times that proposed by Vollenweider (Vollenweider and
        Dillon, 1974) as a eutrophic loading (see page 13).  Because
        of the relatively small contributions, it is not likely that
        point-source phosphorus control would result in any significant
        improvement in the trophic condition of Milford Reservoir.
            2.  Non-point sources—The contribution of non-point sources
        amounted to 96.8% of the total phosphorus load to Milford Reser-
        voir during the sampling year.  The Republican River contributed
        90.8% of the total; Five Creeks, 1.3%; Mall Creek, 0.5%; and the
        ungaged tributaries added an estimated 3.9%.
            The phosphorus export rates of the Republican River, Five
        Creeks, and Mall Creek were 6, 30, and 26 kg/km 2/yr, respectively
        (see page 12).  These rates compare well to those of three tribu-
        taries of nearby Council Grove Reservoir* (60, 41, and 6 kg/km2/
        yr, respectively).
* Working Paper No. 512.

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II.   RESERVOIR AND DRAINAGE  BASIN  CHARACTERISTICS"1"
     A.   Morphometry  :
         1.   Surface area:   65.51  kilometers2.
         2.   Mean depth:   7.8  meters.
         3.   Maximum depth:  21.3  meters.
         4.   Volume:  511.902  x  106 m3.
         5.   Fourteen-year median  hydraulic  retention  time:  285 days.
     B.   Tributary and Outlet:
         (See Appendix C  for flow  data)
         1.   Tributaries  -
                                               Drainage       Mean flow
             Name                              area  (km2)*    (m3/sec)*
             Republican River                   63,563.8         23.530
             Five Creeks                           179.7          0.570
             Mall  Creek                             54.0          0.263
             Minor tributaries &
              immediate drainage -                604.5          2.830
                            Totals             64,402.0         27.193
         2.   Outlet -
             Republican River                   64,465.1**       26.170
     C.   Precipitation***:
         1.   Year of sampling:   66.6 centimeters.
         2.   Mean annual:  87.7  centimeters.
 t Table  of metric  conversions—Appendix B.
 tt Kring,  1977.
 * For limits  of  accuracy,  see Working Paper No. 175, "...Survey Methods,
   1973-1976".
 ** Includes area of  reservoir.
 *** See  Working  Paper  No.  175.

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III.   WATER QUALITY SUMMARY
      Mil ford 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 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 18.0 meters at station  1,  14.0
  meters at station 2, 10.1 meters at station 3, and  4.6  meters at
  station 4.
      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 (MG/L)

CNDCTV/Y  (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)

CHLRPYL  A  (UG/D

SECCHI  (METERS)
                             A. SUMMARY OF  PHYSICAL  AND


                             1ST SAMPLING  (  4/11/74)

                                   <» SITES
                                  CHEMICAL CHARACTERISTICS FOR MILFORO  HESERVOI*
                                   STORtT CODE 2009

                                             2ND SAMPLING  ( 6/26/74)

                                                   4 SITES
     RANGE

  9.0  -  12.5

  9.4  -  10.8

 51S.  -  681.

  8.3  -   8.4

 190.  -  268.

0.112  - 0.271

0.053  - 0.065

0.450  - 1.200

0.040  - 0.150

0.400  - 1.10C

0.500  - 1.270

1.050  - 1.810

 24.4  -  30.7

  0.4  -   0.8
3RO SAMPLING (10/ 3/74)

      4 SITES
MEAN
10.1
10.2
562.
8.4
211.
0.150
0.059
0.879
0.089
0.662
0.968
1.542
26.3
0.6
MEDIAN
9.5
10.3
535.
8.4
204.
0.12*
0.059
1.000
0.080
0.600
1.060
1.600
25.1
0.6
SANGE
20.8
2.2
742.
8.0
192.
0.043
0.013
0.500
0.070
0.500
0.570
1.030
1.1
0.4
- 24.9
8.2
- 861.
8.4
- 228.
- 0.177
- 0.079
- 0.740
- 0.200
- 0.900
- 0.880
- 1.510
- 16.1
2.7
MEAN
23.2
5.6
772.
8.2
199.
0.085
0.040
0.612
0.143
0.637
0.754
1.248
7.3
1.5
MEDIAN
23.1
5.8
753.
8.2
196.
0.066
0.037
0.590
0.140
0.600
0.760
1.280
6.1
1.4
rJANGE
13.4
7.6
630.
8.3
179.
0.017
0.002
0.020
0.020
0.400
0.040
0.530
8.1
0.3
- 17.0
9.0
- 671.
8.6
- 256.
- 0.116
- 0.025
- 0.360
- 0.080
- 0.700
- 0.390
- 1.000
- 51.1
O.t>
MEAN
16.1
8.3
643.
8.4
191.
0.0*2
0.005
0.215
0.030
0.535
0.245
0.750
22.9
0.5
MEDIAN
16.7
8.2
637.
8.4
185.
0.026
0.002
0.220
0.020
0.500
0.240
0.720
16.3
0.6

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B.  Biological Characteristics:

    1.   Phytoplankton -
        Sampling
        Date

        04/11/74
        06/26/74
        10/03/74
Dominant
Genera
1.
2.
3.
4.
5.
1.
2.
3.
4.
5.
1.
2.
3.
4.
5.
Algal Units
peir ml	
   20,
759
801
450
225
135
180
Stephanodiscus sp.
Chroomonas sp.
Ankistrodesmus sp.
Cryptomonas sp.
Nitzschia sp.
Other genera                 180

        Total             23,550

Centric diatoms              284
Microcystis sp.              236
Scenedesmus' sp.              189
Cryptomonas sp.              142
Nitzschia sp.                142
Other genera                 379

        Total              1,372

Stephanodiscus sp.         5,182
Chroomonas sp.               790
Skeletonema sp.              740
Dactylococcopsis sp.         296
Scenedesmus sp.              197
Other genera                 395
                                          Total
                               7,600

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    2.   Chlorophyll  a_ -
Sampling
Date
04/11/74



06/26/74



10/03/74



Station
Number
1
2
3
4
1
2
3
4
1
2
3
4
Chlorophyll a
(yg/1)
24.6
24.4
25.7
30.7
1.1
4.3
7.9
16.1
8.1
16.8
15.8
51.1
C.   Limiting Nutrient Study:

    1.  Autoclaved, filtered, and nutrient spiked -
                         Ortho P
                         Cone, (mg/1)
Inorganic N    Maximum yield
Cone, (mg/1)   (mg/1-dry wt.)
0.025
0.075
0.075
0.025
0.465
0.465
1.465
1.465
12.6
16.3
25.2
13.3
Spike (mg/1)

Control
0.050 P
0.050 P + 1.0 N
1.0 N
    2.  Discussion -

            The control yield of the assay alga, Selenastrum capri-

        cornutum, indicates that the potential  primary productivity

        of Mil ford Reservoir was high at the time the sample was

        taken (04/11/74).   There was a significant increase in yield

        when phosphorus alone was added, but no such increase occurred

        when only nitrogen was added.  These results indicate the

        reservoir was phosphorus limited at that time.

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                         8
    The reservoir data also indicate  phosphorus  limitation.
The mean inorganic nitrogen to orthophosphorus ratios were
16 to 1 in April, 19 to 1  in June,  and  49  to  1 in October;
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  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
 months of 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
 determined by using a modification of  a U.S. Geological Survey computer
 program for calculating stream loadings*.   Nutrient  loads shown are
 those measured minus point-source loads, if any.
     Nutrient loads for unsampled "minor tributaries  and immediate
 drainage" ("ZZ" of U.S.G.S.) were estimated using  the means of the
 nutrient loads, in kg/km2/year, at stations B-l  and  D-l and multi-
 plying the means by the ZZ area in km2.
     The operators of the Clifton, Clyde, Concordia,  and Morganville
 wastewater treatment plants provided monthly effluent samples and
 corresponding flow data.  The operators of the Clay  Center and Wake-
 field wastewater treatment plants provided monthly effluent samples
   See Working Paper No.  175.

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                                    10
but could not provide flow data.  Therefore, nutrient loads from these
two sources were estimated at 1.134 kg P and 3.401  kg N/capita/year,
and flows were estimated at 0.3785 m3/capita/day.
    A.  Waste Sources:
        1.  Known municipal* -

Name
Clay Center

Clifton

Clyde

Concordia

Morganville


Wakefield

Pop.
Served
5,093

714

963

7,680

252


730

Mean Flow
Treatment (m3/d)
prim.
clarifier
Imhoff tank

stab, pond

stab, pond

stab, pond


stab, pond

1,927.7

304.7

529.5

1,063.7

96.9


276.3

Receiving
Water
Republican
River
Republican
River
Republican
River
Republican
River
Buffalo Creek/
Republ ican
River
Mil ford Reser-
voir
        2.  Known industrial - None
* Treatment plant questionnaires.

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                                  11
  B.  Annual Total Phosphorus Loading - Average Year:

      1.   Inputs -

                                            kg P/           %  of
          Source                            yr             total

          a.  Tributaries (non-point load)  -

              Republican River              389,025        90.8
              Five Creeks                     5,355          1.3
              Mall Creek                      2,125          0.5

          b.  Minor tributaries & immediate
               drainage (non-point load) -    16,925          3.9

          c.  Known municipal STP's -

              Clay Center                     5,775          1.3
              Clifton                         1,005          0.2
              Clyde                           1,200          0.3
              Concordia                       5,145          1.2
              Morganville                        75        <0.1
              Wakefield                         830          0.2

          d.  Septic tanks - Unknown            ?             ?

          e.  Known industrial - None

          f.  Direct precipitation* -         1,105          0.3

                      Total                  428,565        100.0

      2.   Outputs -

          Reservoir outlet - Republican River   48,260

      3.   Net annual P accumulation - 380,305 kg.
See Working Paper No.  175.

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                                  12
  C.  Annual Total Nitrogen Loading - Average Year:

      1.  Inputs -

                                            kg N/          % of
          Source                            yr	          total

          a.  Tributaries (non-point load) -

              Republican River            1,884,190         79.7
              Five Creeks                    66,445          2.8
              Mall Creek                     39,140          1.7

          b.  Minor tributaries & immediate
               drainage (non-point load) -  258,120         10.9

          c.  Known municipal STP's -

              Clay Center                    17,320          0.8
              Clifton                         3,445          0.2
              Clyde                           2,710          0.1
              Concordia                      17,365          0.8
              Morganville                       240         <0.1
              Wakefield                       2,485          0.1

          d.  Septic tanks - Unknown            ?            ?

          e.  Known industrial - None

          f.  Direct precipitation* -        68.155          2.9

                      Total               2,359,615        100.0

      2.  Outputs -

          Reservoir outlet - Republican River  1,327,935

      3.  Net annual N accumulation - 1,031,680 kg.

  D.  Non-point Nutrient Export by Subdrainage Area:

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

      Republican River                           6             30
      Five Creeks                               30             370
      Mall Creek                                26             484
See Working Paper No. 175.

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                                13
E.   Mean Nutrient Concentrations in Ungaged Streams:
                                       Mean Total  P      Mean Total  N
    Tributary                          Cone, (mg/1)      Cone,  (mg/1)
    Unnamed Stream C-l                     0.219              2.304
    Unnamed Stream F-l                     1.176
    Unnamed Stream G-1                     0.050              0.170
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 "dangerous1'
    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             6.79       6.02        37.4       16.3
    Vollenweider phosphorus loadings
     (g/m2/yr)  based on mean depth and 14-year median
     hydraulic  retention time of Milford Reservoir:
        "Dangerous"   (eutrophic loading)               0.62
        "Permissible"  (oligotrophic loading)           0.31

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                                    14
V.  LITERATURE REVIEWED

    Kring, R. Lynn, 1977.  Personal  communication  (revised  reservoir
        morphometry).   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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                                15
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

2003  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
431.333
488.500
470.667
445.222
.MEAN
CHLORA
•-J
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
12.800
8.000
13.400
13.000
13.000
13.600
13.400
MEDIAN
DISS CRTHO 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 3Y INDEX NOS.
SANK  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  2003       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

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PERCENT OF LAKES WITH HIGHER VALUES (NUMBER OF LAKES WITH HIGHER VALUES)
LAKE
CODE  LAKE NAME
2001  CEDAR 3LUFF RESERVOIR
2003  COUNCIL GROVE
2003  ELK CITY
2004  FALL RIVER RESERVOIR
2005  JOHN REDMOND RESERVOIR
2006  KANOPOLIS RESERVOIR
2007  MARION RESERVOIR
200ft  MELVERN RESERVOIR
2009  MILFORD 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 1
86 (
57 (
14 1
43 (
64 -I
79 1
21 (
7 I
50 I
71 l
36 i
0 i
93 l
: 14)
: 4)
: 12)
; a)
I 2)
I 6)
! 9)
[ 11)
I 3).
I 1)
I 7)
! 10)
I 5)
( 0)
( 13)
MEDIAN
INORG N
100 <
29 (
50 <
57 <
0 <
43 <
64 1
82 <
36 (
93 1
18 <
7 1
71 (
18 <
82 (
: 14)
: 4>
: 7)
; 8)
: o)
: 6>
: 9)
: ID
; s>
! 13)
: 2>
: i)
I 10)
[ 2)
[ 11)
500-
MEAN SEC
100 (
36 (
7 (
14 (
0 1
29 <
43 <
36 1
79 <
64 (
57 1
50 <
21 1
71 l
93 1
i 14)
: 5)
; i)
: 2)
; o)
: 4)
: 6)
: 12)
: ID
: 9>
I 8)
! 7)
I 3)
[ 10)
I 13)
MEAN
CHLORA
93 (
43 1
100 (
71 (
50 1
21 (
29 1
0 1
14 1
7 1
86 1
64 1
79 i
36 i
57 1
: 13)
; 6)
: 14)
: 10)
: 7)
; 3)
1 4)
t 0)
I 2)
[ 1)
I 12)
1 9)
t 11)
( 5)
[ 8)
15-
MIN DO
57 1
64 {
7 (
79 1
93 1
71 (
86 1
0 1
50 1
100 1
25 1
39 1
39 i
14 .1
25 l
: a)
: 9)
; i>
: ID
; 13)
: io>
[ 12)
; o
; 7)
[ 14)
[ 3)
[ 5)
! 5)
( 2)
; 3)
MEDIAN
DISS ORTHO P
89 <
29 1
100 <
50 (
7 1
64 (
71 1
79 1
14 1
21 (
43 l
36 1
57 <
0 <
89 1
: 12)
: 4)
; 14)
; 7)
; i)
; 9)
[ 10)
: ID
[ 2)
[ 3)
[ 6)
[ 5)
C 8)
t 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
                                                                                           12/0376
     CODE 2009
                   MILFORD
     TOTAL DRAINAGE AREA OF LAKE(SO KM)
          SUB-ORAINA'3E
TPI6UTAKY  ARfAfSQ KM)
                                                                NORMALISED  FLO*S(CMS>
2009A1
2009A2
2009B1
200901
2009ZZ
           64465.1
           63563.8
             179.7
              54.0
             614.9
JAN
12.16
10.76
0.24
0.113
1.27
Ftb
20.95
17.56
0.34
0.150
1.67
MAR
24.64
0.74
0.368
3.11
APH-
36.61
23.50
0. 71
0.311
3.68
MAY
45.31
33.96
1.02
0.461
3.11
J'JN
39.64
42.46
1.06
0.453
3.40
JUL . AUG SEP
23.03 17.27 23.22
33. 98 19.62 31.15
1.05 0.34 0.40
0.510 0.150 0.173
b.38 3.11 3.40
OCT
15.57
23.22
0.48
0.216
2.83
NOV
19.54
12.18
0.23
0.099
1.64

13
0
0.
1
•JEC
.03
!24
116
.30
MEAN
26.17
23.53
0.57
0.263
2.H3
SUMMARY
TOTAL
SUM OF
DRAINAGE AREA OF LAKE =
SUB-DRAINAGE AREAS »
64439.2
64412.4

TOTAL FLOW IN =
TOTAL FLOW OUT =
326.
314.
24
03



     MEAN MONTHLY FLOWS AND DAILY FLOwS(CMS)

TRIBUTARY   MONTH   YEAR    MEAN FLOW  DAY

2009A1
                                                   FLO*1  DAY
                                                                     FLOW  DAY
                                                                                       FLOW
2009A2
10
11
12
1
2
3
4
5
6
7
8
9
10
11
12
1
2
3
4
5
6
7
8
9
74
74
74
75
75
75
75
75
75
75
75
75
74
74
74
75
75
75
75
75
75
75
75
75
7.419
2.053
1.444
1.317
3.908
16.197
9.231
4.870
58.333
56.917
9.401
2.240
4.389
6.315
6.173
6.116
6.4CO
16.339
11.525
7.051
75.040
23.701
10.449
4.786
12
e
14
11
8
9
24
Ib
20
12
30
29
12
16
8
5
2
1
13
4
8
6
10
6
12.743
2.067
1.331
1.246
1.331
26.674
9.345
2.464
85.517 30
127.426 30
3.455
2.124
3.964
6.?86
6.966
4.672
5.267
25.485
9.514
8.948
30.016 20
38.794 20
9.401
8.155








55.218
8.297










104.772
11.893



-------
                                   TRIBUTARY FLOW  INFORMATION FOR KANSAS
                                                                                           12/0376
LA^ONTH   YEA*
200901
2009Z2
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
74
74
74
75
75
75
75
75
75
75
75
75
7t
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
0.150
0.241
0.263
3.233
0.311
0.425
0.680
0.212
2.520
0.340
0.156
0.096
0.068
0.102
0.125
0.110
0.139
0.212
0.283
0.099
1.048
U.164
0.068
0.042
0.878
.699
.416
.246
.529
.812
3.398
0.651
7.929
1.727
1.416
0.821
1?
16
6
5
2
1
13
4
8
6
10
6
12
16
8
S
2
1
13
4
8
6
10
6












                                                   FLOW  DAY
                                                                      rLOw  DAY
                                                                                       FLOW
O.OlH
O.OuO
0.054
0.054
0.037
0.198
0.127
0.085
1.133
0.139
0.031
0.042
0.076
0.074
0.071
O.ObS
0.062
0.071
0.035
0.095
0.071
0.057
0.040
0.042








20
20










16
20


                                                                    7.079
                                                                    0.065
                                                                    0.0
                                                                    0.057
                                                                            20
0.127

-------
        APPENDIX D





PHYSICAL and CHEMICAL DATA

-------
STORET RETRIEVAL DATE 76/05/03
                                                                   200901
                                                                  39 04  40.0  096 53 51.0 3
                                                                  MILFURD  RESERVOIR
                                                                  20.061    KANSA.S
                                                                                           091191
                                                                  11EPALES             2111202
                                                                   0042  FEET   DEPTH  CLASS 00
DATE
FROM
TO
74/04/11



74/06/26




74/10/03





DATE
FROM
TO
74/04/11



74/06/26




74/10/03




TIME DEPTH
OF
DAY FEET
15 00 0000
15 00 0005
15 00 0015
15 00 0037
13 00 0000
13 00 0005
13 00 0022
13 00 0040
13 00 0059
09 05 0000
09 05 0005
09 05 0015
09 05 0030
09 05 0040

TIME DEPTH
OF
DAY FEET
15 00 0000
15 00 0005
15 00 0015
15 00 0037
13 00 0000
13 00 0005
13 00 0022
13 00 0040
13 00 0059
09 05 0000
09 05 0005
09 05 0015
09 05 0030
09 05 0040
00010
WATER
TEMP
CENT
9.1
9.1
9.0
9.0
23.1
23.1
22.5
22.1
20.8
16.9
16.9
16.9
16.9
17.0
00665
PHOS-TOT

MG/L P
C.114
0.113
0.113
0.112
0.075
0.045
0.046
0.083
0.104
0.026
0.026
0.017
0.072
0.026
00300
DO
MG/L

10.
10.
10.
6.
6.
5.
4.
2.
7.
7.
7.
8.
7.
32217
00077 00094
TRANSP CNDUCTVY
SECCHI FIELD
INCHES MICROMHO
30
4
4
2
8 108
6
4
8
2
8 24
8
8
0
6
00031
517
517
516
515
749
750
747
742
743
643
642
645
645
645

00400 00410
PH T ALK
CAC03
SU
8.35
8.4Q
8.40
8.40
8.30
8.30
8.20
8.20
8.10
8.27
8.29
8.31
8.27
8.25

MG/L
212
202
210
204
195
195
198
201
202
185
186
183
186
188

00610 00625 00630 00671
NH3-N TOT KJEL N02&N03 PriOS-DIS
TOTAL N N-TOTAL ORTHO
MG/L
0.080
0.080
0.070
0.100
0.120
0.100
0.130
0.130
0.140
0.020K
0.020K
0.020K
0.020K
0.030

MG/L
0.600
0.400
0.500
0.500
0.600
0.500
0.500
0.600
0.500
0.700
0.500
0.400
0.500
0.500

MG/L
1.140
1.060
1.200
1.110
0.680
0.590
0.640
0.710
0.740
0.300
0.360
0.220
0.360
0.360

MG/L P
0.059
0.062
0.063
0.062
0.070
0.026
0.031
0.039
0.046
0.002
0.004
0.004
0.025
0.015

CHLRPHYL INCDT LT
A O C' U M T fc 1 fl.
UG/L
24.



1.




8.




HEMNING
PERCENT
6



1

1.0


1




















































































































          K VALUE KNO*N TO BE
          LESS THAN INDICATED

-------
STORET RETRIEVAL DATE 76/05/03
                                                                  300902
                                                                 39 07 33.0 096 54 57.0 3
                                                                 MILFORD RESERVOIR
                                                                 20061   KANSAS
                                                                                          091191
                                                                 11EPALES             2111202
                                                                  0050 FEET  DEPTH  CLASS 00
DATE
FROM
TO
74/04/11




74/06/26




74/10/03





DATE
FROM
TO
74/04/11




74/06/26




74/10/03




TIME DEPTH
OF
DAY FEET
14 35 0000
14 35 0005
14 35 0015
14 35 0030
14 35 0045
13 30 0000
13 30 0005
13 30 0020
13 30 0030
13 30 0041
09 40 0000
09 40 0005
09 40 0015
09 40 0030
09 40 0046

TIME DEPTH
OF
DAY FEET
14 35 0000
14 35 0005
14 35 0015
14 35 0030
14 35 0045
13 30 0000
13 30 0005
13 30 0020
13 30 0030
13 30 0041
09 40 0000
09 40 0005
09 40 0015
09 40 0030
09 40 0046
00010
WATER
TEMP
CENT
9.5
9.4
9.5
9.4
9.4
23.8
23.1
23.0
22.6
22.4
16.8
16.7
lt>.8
16.7
16.7
00665
PHOS-TOT

MG/L P
0.126
0.130
0.119
0.120
0.123
0.045
0.044
0.045
0.043
0.060
0.019
0.024
0.026
0.025
0.036
00300 00077
DO TRANSP
SECCHI
MG/L INCHES
25
10.4
10.6
10.8
10.4
7.6 72
7.0
6.6
6.0
4.6
8.4 24
8.4
8.2
8.2
8.0
32217 00031
CHLRPHYL INCOT LT
A REMNING
UG/L PERCENT
24.4

,


4.3

1.0


16.8




00094
CNDUCTVY
FIELD
MICROMHO
521
521
523
523
547
753
747
744
743
742
637
636
637
637
636



















00400
PH

SU
8.
8.
8.
a.
8.
8.
8.
8.

8.
8.
8.
8.
8.
8.





















40
40
40
40
40
40
40
30

00
36
35
38
37
34



















00410
T ALK
CAC03
MG/L
196
200
192
204
204
193
194
196
192
198
185
185
182
179
180



















00610 00625
NH3-N TOT KJEL
TOTAL
MG/L
0.060
0.060
0.060
0.080
0.100
0.070
0.130
0.130
0.130
0.150
0.020K
0.020K
0.020K
0.020K
0.060



















N
MG/L
0.800
0.600
0.600
0.600
0.700
0.600
0.500
0.500
0.500
0.600
0.600
0.600
0.600
0.400
0.400



















00630
N02&N03
N-TOTAL
MG/L
1.010
1.030
0.990
1.050
1.010
0.500
0.530
0.580
0.540
0.630
0.250
0.310
0.200
0.180
0.300



















00671
PHOS-DIS
ORTHO
MG/L P
0.059
0.061
0.060
0.059
0.057
0.013
0.023
0.032
0.025
0.036
0.003
0.002
0.003
0.002
0.002



















           K VALUE KNOrfN TO 3E
           LESS THAN INDICATED

-------
STORET RETRIEVAL DATE 76/05/03
  DATE   TIME DEPTH
  FROM    OF
   TO    DAY  FEET
74/04/11 14
         14
         14
         14
74/06/26 14
         14
         14
         14
         14
74/10/03 10
         10
         10
         10
15 0000
15 0005
15 0015
15 0030
00 0000
00 0005
00 0015
00 0025
00 0033
15 0000
15 0005
15 0015
15 0025
 00010
HATER
 TEMP
 CENT

   10.1
   10.0
   10.0
   10.0
   23.5
   23.4
   23.2
   23.0
   22.5
   16.1
   16.1
   16.0
   16.0
                                                                  200903
                                                                 39  11  14.0 096 59 09.0  3
                                                                 MILFORD RESERVOIR
                                                                 20061   KANSAS
                                                                                          091191
11EPALES
211
0035 FEET DEPTH CLASS
00300
DO
MG/L

10.2
10.2
10.2
5.8
6.0
5.2
3.8
2.2
8.4
8.4
8.6
8.2
00077
TRANSP
SECCHI
INCHES
20



36




24



00094
CNDUCTVY
FIELD
MICROMHO
565
564
564
565
770
770
765
760
754
630
631
631
631
00400
PH
su
8.35
8.30
8.30
8.30
8.4Q
8.20
8.20
8.10
8.00
8.44
8.41
8.42
8.45
00410
T ALK
CAC03
MG/L
202
198
204
190
196
194
194
194
195
181
181
180
182
00610
NH3-N
TOTAL
MG/L
0.140
0.150
0.140
0.150
0.150
0.140
0.160
0.160
0.200
0.080
0.020
0.020
0.030
1202
00
00625
TOT KJEL
N
MG/L
0.600
0.800
0.800
0.900
0.700
0.600
0.700
0.700
0.700
0.600
0.500
0.500
0.400


00630
N02&N03
N-TOTAL
MG/L
0.730
0.770
0.760
0.750
0.580
0.570
0.580
0.600
0.630
0.220
0.180
0.190
0.130


00671
PHOS-DIS
OftTrtO
MG/L P
0.053
0.054
0.055
0.055
0.037
0.034
0.034
0.037
0.040
0.002K
0.002K
0.002K
0.002K

DATE
FROM
TO
74/04/11



74/06/26





74/10/03




TIME DEPTH
OF
DAY FEET
14 15 0000
14 15 0005
14 15 0015
14 15 0030
14 00 0000
14 00 0005
14 00 0008
14 00 0015
14 00 0025
14 00 0033
10 15 0000
10 15 0005
10 15 0015
10 15 0025
00665 32217 00031
PHOS-TOT CHLRPHYL INCDT LT
A REMNING
MG/L P UG/L PERCENT
0.133 25.7
0.126
0.120
0.158
0.068 7.9
0.066
1.0
0.065
0.068
0.100
0,022 15.8
0.029
0.023
0.030
         K VALUE KNOWN TO BE
         LESS THAN INDICATED

-------
STORE! RETRIEVAL DATE 76/05/03
  DATE   TIME DEPTH
  FROM    OF
   TO    DAY  FEET
74/04/U 13 50
         13 50
         13 50
74/06/26 14 20
               0000
               0005
               0010
               0000
         14 20 0005
         14 20 0010
         14 20 0015
74/10/03 10 45 0000
         10 45 0005
         10 45 0012
 00010
MATER
 TEMP
 CENT

   12.5
   12.5
   12.4
   24.8
   24.9
   24.1
   24.0
   13.5
   13.5
   13.4
                                                                  200904
                                                                 39 13 01.0 097 00 15.0 3
                                                                 MILFOSD RESERVOIR
                                                                 20027   KANSAS
                                                                                          091191
11EPALES
2111202
0015 FEET DEPTH CLASS
00300
DO
MG/L

9.4
9.8
7.6
8.2
5.6
5.2
9.0
9.0
8.6
00077
TRANSP
SECCHI
INCHES
14


15



12


00094
CNDUCTVY
FIELD
MICHOMHO
681
681
679
838
847
849
861
670
669
671
00400
PH
SU
8.30
8.35
8.30
8.40
8.40
8.20
8.10
8.57
8.53
8.57
00410
T ALK
CAC03
MG/L
268
254
236
199
200
228
226
214
216
256
00610
NH3-N
TOTAL
MG/L
0.040
0.060
0.050
0.130
0.180
0.170
0.190
0.020
0.020
0.070
00
00625
TOT KJEL
N
MG/L
1.100
0.500
0.600
0.900
0.800
0.800
0.800
0.700
0.600
0.600

00630
N-TOTAL
MG/L
0.460
0.550
0.450
0.550
0.580
0.710
0.680
0.020K
0.050
0.020K

006M
PMOS-; IS
OR Trie
MG/L P
0.05*
0.065
0.059
0.039
0.054
0.079
0.064
0.002K
0.006
0.003
DATE
FROM
TO
74/04/11


74/06/26




74/10/03


00665 32217 00031
TIME DEPTH PHOS-TOT CHLRPHYL INCDT LT
OF A REMNING
DAY FEET
13
13
13
14
14
14
14
14
10
10
10
50
SO
50
20
20
20
20
20
45
45
45
0000
0005
0010
0000
0003
0005
0010
0015
0000
0005
0012
MG/L P UG/L PERCENT
0
0
0
0

0
0
0
0
0
0
.252 30.7
.271
.265
.142 16.1
1.0
.160
.176
.177
.085 51.1
.104
.116
          K  VALUt KNOWN TO BE
          LESS  TH0N INDICATED

-------
       APPENDIX E

TRIBUTARY AND WASTEWATER
  TREATMENT PLANT DATA

-------
STORE! RETRIEVAL DATE 76/05/C4
                                                                  39  04  15.0  096 52 00.0  4
                                                                 20       7.5 JUNCTION CTY
                                                                 0/MILFOSD *ESE^VulK   .    091191
                                                                 US rl«Y  77 S-DG  3 MI Nw OF  JUNCTION  CITY
                                                                 llEPALtS             2111204
                                                                  0000 FEET  DEPTn  CLAiS  00
DATE
FROK
TO
74/10/12
74/11/08
74/12/14
75/03/09
75/04/24
75/05/15
75/06/20
75/06/30
75/07/12
75/07/30
75/09/29
00630 0062S
TIME DEPTH N02&N03 TOT KJEL
OF N-TOTAL N
DAY FEET
09
13
09
09
13
10
08
06
09
10
09
10
30
00
00
00
00
50
00
15
00
00
MG/L
0
0
0
0
0
0
0
0
0
0
0
.312
.272
.224
.235
.035
.020
.170
.290
.140
.320
.420
HG/L
2.
1.
1.
0.
1.
0.
0.
1.
1.
0.
0.
300
800
700
900
650
650
600
450
700
850
700
00610 00671 00665
NH3-N PHOS-OIS PHOS-TOT
TOTAL GRTHO
MG/L
3.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
C90
04S
030
100
055
025
075
055
025
090
035
MG/L P
0
0
0
0
0
0
0
0
0
0
0
.040
.040
.035
.024
.015
.030
.020
.035
.020
.085
.055
MG/L P
0.065
0.140
0.100
0.040
0.040
0.080
0.040
0.050
0.050
0.14&
0.100

-------
STJPET RETRIEVAL DATE 7o/os/o<»
  OATE   TIME OEPTrt N02&N03
  FROM    Of
   TO    DAY  FEET
7W10/12
7^/11/16
7<+/12/08
75/01/05
75/03/02
75/03/01
75/0^/13
75/OS/0<.
75/06/08
75/06/20
75/07/06
75/07/20
75/08/10
13 55
15 30
13 30
13 00
15 30
16 <»0
11 ?0
10 10
11 15
11 50
10 45
10 35
10 00
                                                                   2009A2
                                                                  39 21  15.0 097 08 <»5.0 <*
                                                                  20      CLAY CO HWr MAP
                                                                  T/Mt._FORD RESEKvOlK      091191
                                                                  AT STATE H*r 15 BPuii
                                                                  UE°iL£S             211120^
                                                                   0000 FEET  DEPTH  CLASS 00
0630
AND 3
OTAL
iG/L
0.016
0.790
1.C60
1.060
0.890
1.^00
0.005
0.005
1.500
0.930
0.510
0.010
0.010
00625
TOT KJEL
N
MG/L
2.300
1.100
1.500
2.200
1.000
3.300
2.500
1.650
1.080
0.500
1.750
1.250
3.600
00610
NH3-N
TOTAL
MO/L
0.0^0
C.100
0.115
0.176
0.088
0.?92
0.035
0.025
0.035
0.1 2C
0.020
0.020
0.130
00671
PHOS-OIS
GSTriO
MG/L r
0.230
0.280
0.250
0.210
0. 168
0.22*
0.185
0.095
0.270
0.185
0.195
0.115
0.085
00665
PnOS-TOT

MG/L P
U.380
0.300
0.300
0.230
0.190
0.750
0.300
O.J20
0.510

O.S60
0.330
0.
-------
STORE! RETRIEVAL DATE 76/05/04
DATE
FROM
TO
74/10/12
74/11/16
74/12/Ofl
75/01/05
75/02/02
75/03/01
75/04/13
75/05/0<+
75/06/08
75/06/20
75/07/06
75/07/20
75/OS/10
TI«E 1
OF
DAY
13 ?5
K 05

13 45
14 15
15 45
11 00
13 50
11 00
11 30
10 20
11 00
10 00
              FEET
                                                                  39  21  00.0  097  12  15.0  4
                                                                  FIVE  CHEEKS
                                                                  20       CLAY  CO  nwr  MAP
                                                                  TfMltfjPD «ES£^VO'!M       091191
                                                                  AT  cHOCi  ON  E-rf CO  «D
                                                                  llEPiLES             3111204
                                                                   oooo  FEET  OE^TH  CLASS oo
0630
!&N03
'OTAL
IG/L
0.112
0.200
0.083
0.096
0.200
1.375
0.230
0.220
0.500
0.390
0.180
0.1*0
0.190
00625
TOT KJEL
N
MG/L
0.800
1.500
1.600
0.500
0.400
2.900
3.300
1.750
1.400

4.000
0.550
0.950
00610
Nn3-N
TOTAL
MG/L
0.040
0.060
0.055
0.136
0.016
0.236
0.140
0.070
0.320
0.075
0.050
O.C40
0.060
00671
PriOS-OIS
OSTHO
MG/L P
0.030
0.035
0.040
0.025
0.016
0.116
0.065
0.050
0. 100
0.240
0.070
0.050
0.050
00665
PhOS-TOT

M(3/L P
0.110
0.110
0.070
0.030
0.04Q
C.330
0.140
0.120
0.330

0.160
0.090
0.160

-------
STORET RETRIEVAL  DATE 76/05/04
                                                                    200VC1
                                                                   39 22 52.0 097 03 15.0 4
                                                                   UNNAMtO  STREAM
                                                                   20      7.5 CL4r CcN Nv»
                                                                   T/MlLFORO SESERvOI*      091191
                                                                   US nwt  2<* 6RDG IN CLAV CENTER
                                                                   11EJ4'-£S             211120'.
                                                                    0000 FEET  DEi^Tn  CLASS 00
DATE
FROM
TO
74/10/12
74/1 1/16
74/12/08
75/01/05
75/02/02
75/03/01
75/04/13
75/05/04
75/06/08
75/06/20
75/07/06
75/07/19
75/08/10
75/09/06
OC630 00625
TIME DEPTH N02kN03 TOT KJEL
OF N-TuTAL N
DAY FEET
13
15
13
10
11
13
09
16
11
11
10
15
08
15
00
28
15
00
15
00
40
20
27
00
00
30
35
25
MG
C
0
0
0
0
1
0
0
1
0
0
0
0
1
XL
.016
.216
.660
.480
.624
.465
.155
.060
.570
.560
.420
.240
.430
.050
MG/L
1
1
2
1
3
4
2
1
1
0
0
0
1
0
.700
.ICO
.050 .
.200
.800
.600
.000
.450
.900
.060
.800
.750
.950
.750
00610
NM3-N *
TOTAL
MG/L
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
C40
040
045
176
032
591
055
070
POO
060
C30
017
060
C45
00671 006&5
Jn03-DIS PhOS-TOT
cm HO
MG/L
0.
0.
0.
0.
0.
0.
<).
0.

0.
0.
0.
0.
?.
p
080
045
030
015
029
432
135
085

005
155
265
250
315
MG/L P
0.165
0.140
0.070
0.050
0.070
0.730
0.230
0.130
0.230
0.010K
0.220
0.315
0.32G
0.39o
  K VALUE KNOWN  TO BE
  LESS  THAN  INDICATED

-------
STOHET RETRIEVAL DATE 76/05/04
  DATE   TIME OEDTH N02J.N03
  FROM    OF
   TO    DAY  FEET
7^/10/12
74/12/08
75/01/05
75/02/02
75/03/01
75/04/13
75/05/0^
75/06/03
75/06/20
75/07/20
75/0(4/10
75/09/06
14 30
15 30
15 30
08 52
11 10
13 45
10 00
16 35
16 15
16 30
10 10
12 30
15 10
                                                                   200901
                                                                  39 lo 52.0 096 59  49.0  4
                                                                  MALL CHEEK
                                                                  20      7.5 6ALA
                                                                  T'/MiLFOSb *ESc*vO"H       091191
                                                                  SEC «0 130 citfOG 3.2 MI  ESE  OF  Br?OUGrlTON
                                                                  llE-iLtb              2111204
                                                                   OOOJ FEET  DEPTH  CLASS  00
0630
'J.N03
OTAL
IG/L
1.840
1.920
2.080
2.160
2.240
3.160
1.720
1.000
2.300
1.880
1.600
1.570
1.600
00625
TOT KJEL
N
MG/L
2.000
0.800
1.600
1.800
2.400
6.300
1.600
1.250
1.250
3.800
2.000
6.600
1.000
00610
NH3-N
TOTAL
MG/L
0.045
0.065
0.020
0.192
0.024
0.77C
0.075
0.115
0.125
0.120
0.070
0.090
0.045
00671
PhOS-DIS
ORTHO
MG/L P
0.060
0.045
0.060
0.07S
0.092
0.248
0.135
0.115
0.115
0.165
0.175
0.110
0.125
00665
PMOS-TOT

MG/L f>
0.190
0.090
0.070
0.120
0.130
0.925
0.210
0.200
0.340
0.350
0.580
0.290
0.220

-------
ST.ORET RETRIEVAL DATE  76/05/04
                       00630      00625     00610      00671
  DATE   TIME DEPTH N02J.N03    TOT  KJEL    Nr(3-N     PhOS-OIS
  FROM    OF        N-TOTAL      N       TOTAL      ORTHO
   TO    DAY  FEET     MG/L       MG/L       MG/L      MG/L P
                                                                   2009F1
                                                                  39 11 30.0 097 02 07.0 4
                                                                  UNNAMED CREEK
                                                                  20      7.5 rfA*EFI£LD
                                                                  T/MILFOKD KESERVOIrJ      091191
                                                                  SEC *0 BRDG 2 MI S« OF «(AKEFIELD
                                                                  IIEP^LES             2111204
                                                                   oooo FEET  DEPTH  CLASS uo
                   00665
                 PHOS-TOT

                  MG/L P
75/04/24 13 30
                        0.390
0.170
0.970
1.176

-------
STORE! RETRIEVAL DATE 76/05/04
                      00630     00625     00610
  DATE   TIME DEPTH N02J.N03   TOT KJEL   NM3-N
  PROM    OF        N-TOTAL      N       TOTAL
   TO    DAY  FEET    MG/L      MG/L      MG/L
                                                                  2009G1
                                                                 39 10 20.0 097 02 07.0 4
                                                                 UNNAMEO CREEK
                                                                 20      7.5 WAKEFIELD
                                                                 T/MILFORO RESERVOIK      091191
                                                                 SEC RO BRDO 3.4 MI SSW OF WAKEFIELD
                                                                 11EPALES             2111204
                                                                  OCOO FEET  DEPTH  CLASS 00  •
                             00665
                           PHOS-TOT
  00671
PHOS-DIS
 ORTHO
 MG/L P    MO/L
75/04/24 13 10
                       0.005
0.165
                                           0.165
                    0.045
                                                               0.050

-------
STORET RETRIEVAL DATE 76/05/04
  DATE   TIME DEPTH N02&N03
  FROM    OF
   TO    DAY  FEET
 75/01/20
 75/02/17
 75/03/26
 75/04/30
 75/05/12
 75/07/25
 75/10/24
 75/11/21
 75/12/03
 75/12/22
 76/01/14
 76/02/04
10 30
09 30
08 30
09 45
09 00
14 30
11 00
09 00
08 30
12 30
08 45
08 45
                                                                  2009AA          PR2009AA     P000714
                                                                 39 33 30.0 097 19 30.0 4
                                                                 CLIFTON
                                                                 20      7.5 CLIFTON
                                                                 T/MILFORD RES            091191
                                                                 REPUBLICAN RIVER
                                                                 11EPALES             2141204
                                                                  0000 FEET  DEPTn  CLASS 00
0630
&N03
OTAL
IG/L
0.080
0.080
0.100
0.050
0.050
0.075
0.050
0.050
0.175
0.025
1.600

00625
TOT KJEL
N
MG/L
32.500
21.000
16.000
50.000
19.000
24.000
45.000
23.000
35.000
42.500
27.000
27.000
00610
NH3-N
TOTAL
MG/L

5.300
4.300
26.300
4.600
10.000
25.000
8.900
20.000
24.000
12.000

00671
PhOS-OIS
ORTrlO
MG/L P
5.900
4.000
3.600
3.600
3.100
5.400
5.400
5.200
9.500
7.600
5.600

00665
PHOS-TOT

MG/L P
8.100
6.000
5.600
12.500
5.500
11.500
10.000
7.000
13.500
8.450
9.400
10.000
50051
FLOW
RATE
INST MGD
0.100
0.075
0.070
0.074
0.068
0.071

0.072
0.087
0.075
0.096
0.078
50053
CONDUIT
FLOW-MGD
MONTHLY
0.100
0.077
0.080
0.078
0.092
Oo068
0.071
0.072
0.084
0.071
0.095
0.078

-------
STORET RETRIEVAL DATE 76/05/04
DATE
FROM
TO
75/01/06
CP < T > -
75/01/06
75/02/04
CP(T)-
75/02/04
75/03/04
CP(T>-
75/03/04
75/04/07
CP(T)-
75/04/07
75/05/06
CP(T>-
75/05/06
75/06/03
75/07/14
CP(T)-
75/07/14
75/08/03
CP
-------
STORE! RETRIEVAL DATE 76/05/04
                      00630     00625
  DATE   TIME DEPTH N02&N03   TOT KJEL
  FROM    OF        N-TOTAL      N
   TO    DAY  FEET    MG/L      MG/L
75/02/18 11 00
CP < T > -
75/02/18 16 00
75/03/16 08 00
CP(T)-
75/03/16 16 00
75/04/15 08 00
CP-
75/04/15 16 00
75/05/06 08 00
CP-
75/05/06 17 00
75/05/27 09 00
CP(T)-
75/05/27 16 00
75/06/17 08 00
CP(T)-
75/06/17 15 00
75/07/08 08 00
CP(T>-
75/07/08 17 00
75/07/29 07 00
CP-
75/07/29 17 00
75/08/19 08 00
CP-
75/08/19 18 00
75/09/09 08 00
CP(T)-
75/09/09 17 00
75/09/30 08 00
CP(T)-
75/09/30 17 00
75/10/21 08 00
CP(T)-
75/10/21 17 00
                                                                  2009AC          PR2009AC     P0050^3
                                                                 39 21 40.0 097 07 30.0 4
                                                                 CLAY CENTER
                                                                 20      7.5 CLAY CENTER
                                                                 T/MILFORO RESERVGIK      091191
                                                                 REPUBLICAN RIVER
                                                                 UEPALES             2141204
                                                                  0000 FEET  DEPTH  CLASS 00

                                          00610     00671     00665     50051     50053
                                         NH3-N    PHOS-OIS  PHOS-TOT    FLOW    CONDUIT
                                         TOTAL     ORTHO                RATE    FLOW-MGD
                                          MG/L     MG/L P    MG/L P   INST MOD  MONTHLY
                                                                         0.005
0.880
0.320
0.050
0.350
1.050
0.150
2.750
1.450
1.570
1.950
0.025
0.275
21.000
18.000
19.500
16.500
16.000
16.500
9.700
8.200
11.000
9.200
19.000
21.000
8.100
11.600
10.000
4.300
4.700
4.900
0.140
0.450

0.200
6.400
8.300
2.800
5.000
3.300
2.900
3.200
0.900
1.720
2.300
2.100
2.100
4.300
4.100
5.200
6.000
5.600
5.100
3.700
4.800
2.800
2.900
3.300
2.900
5.800
5.800

-------
STORET RETRIEVAL DATE 76/05/04
                      00630
  DATE   TIME DEPTH N02^N03
  FROM    OF        N-TOTAL
   TO    DAY  FEET    MG/L
75/11/16 08 00
CP(T>-
75/11/16 16 00
0.075
34.000
                                           2009AC          Ph!2009AC
                                          39 21  40.0 097 07 30.0 4
                                          CLAY CENTER
                                          20      7.5 CLAY CENTEW
                                          T/MILFO'RD RESEKVOiS
                                          REPUBLICAN RIVER
                                          IIE^ALES             2141204
                                           0000  FEET  DEPTrt  CLASS 00
                                                                                               PQ05093
00625
TOT KJEL
N
MG/L
00610
NH3-N
TOTAL
MG/L
00671
PhOS-OIS
ORTHO
MG/L P
00665
PHOS-TOT

MG/L P
50051
FLOW
RATE
INST MGO
50053
CONDUIT
FLOW-MGO
MONTHLY
10.500
                              5.000
                               9.800

-------
STORET RETRIEVAL DATE 76X05/04
  DATE   TIME DEPTH N02&N03
  FROM    OF
   TO    DAY  FEET
75/02/10
75/03/12
75/04/11
75/04/29
75/05/19
75/06/04
75/06/30
75/07/29
75/09/24
75/10/20
75/11/06
75/12/02
75/12/22
15 35



16 40
14 25
15 15
14 00

00 00
15 00
16 10
00 00
                                                                  2009AD          P02009AD     P000963
                                                                 39 35 00.0 097 24 00.0 4
                                                                 CLYDE
                                                                 20      7.5 CLYDE
                                                                 T/MILFORD RESERVOIR      091191
                                                                 REPUBLICAN RIVER
                                                                 11EPALES             2141204
                                                                  0000 FEET  DEPTH  CLASS 00
0630
'{.N03
OTAL
IG/L
0.160
0.160
1.200
0.050
0.150
0.150
0.025
0.025
0.050
0.425
0.675
0.950
1.200
00625
TOT KJEL
N
MG/L
3.000
7.000
21.000
22.000
30.000
18.000
9.000
11.500
11.500
8.200
9.100
6.300
7.700
00610
NH3-N
TOTAL
MG/L
1.550
5.900

8.000
0.290
1.250
0.120
0.025K
0.175
0.035
0.025K
0.200
0.250
00671
PMOS-DIS
ORTHO
MG/L P
6.530
6.000

7.400
7.900
9.400
7.030
2.100
3.800
4.175
4.500
4.300
5.700
00665
PHOS-TOT

MG/L P
7.080
6.900
8.100
9.200
9.400
10.200
7.300
2.500
4.800
5.200
5.700
5.400
6.400
50051
FLOW
HATE
INST MOD


0.100

0.150
0.150
0.160
0.300
0.100
0.150
0.120

0.144
50053
CONDUIT
FLOW-MGD
MONTHLY




0.150
0.115

0.250
0.100
0.130
0.125

0.129
    K VALUE KNOWN TO BE
    LESS THAN INDICATED

-------
STORET RETRIEVAL DATE 76/05/04
  DATE   TIME DEPTH N02&N03
  FROM    OF
   TO    DAY  FEET
75/03/06
75/04/03"
75/05/01
75/05/23
75/06/12
75/07/07
75/07/24
75/08/07
75/09/28
75/09/18
75/10/19
75/10/29
11
11
11
11
11
11
11
11
11
11
11
11
IS
30
00
30
30
30
30
30
30
30
30
30
                                                                  20C9AE          P02009AE     P007680
                                                                 39 34 40.0 097 38 00.0 4
                                                                 CONCORD I A
                                                                 20      7.5 COHCORDIA
                                                                 T/MILFORO RES.           091191
                                                                 REPUBLICAN RIVER
                                                                 HEPALES             2141204
                                                                  0000 FEET  DEPTH  CLASS 00
0630
&N03
OTAL
G/L
0.160
0.240
0.050
0.050
0.050
0.025
0.050
0.100
0.075
0.025
0.075
0.025
00625
TOT KJEL
N
MG/L
53.000
45.000
65.000
46.000
48.300
28.000
37.000
33.000
40.000
47.000
48.000
46.000
00610
NH3-N
TOTAL
MG/L
22.000
18.400
25.000
22.500
19.950
14.000
14.500
13.500
17.500
24.000
26.500
24.500
00671
PHOS-DIS
ORTHO
MG/L P
5.520
4.900
3.200
4.000
3.800
6.100
^.SOO
2.500
7.800
8.800
3.200
4.400
00665
PHOS-TOT

MG/L P
17.500
14.500
19.500
16.000
15.500
9.200
5.700
13.000
12.800
11.000
25.000
16.500
50051
FLOW
RATE
INST MGD
0.266
0.300
0.246
0.202
0.222

0.518
0.270
0.300



50053
CONDUIT
FLOW-MOD
MONTHLY
0.272
0.300
0.225
0.200
0.211

0.500
0.265
0.275




-------
STOPET RETRIEVAL DATE 76/07/12
                      00630
  DATE   TIME DEPTH N02&N03
  FROM    OF        N-TOTAL
   TO    OAY  FEET    MG/L
75/04/24 13 30
0.390
                                                                  2009F1
                                                                 39 11 30.0 097 02 07.0 4
                                                                 UNNAMED CREEK
                                                                 20      7.5 WAKEFIELD
                                                                 T/MILFORD RESERVOIR      091191
                                                                 SEC RO BRDG 2 MI SW OF WAKEFIELD
                                                                 11EPALES             2111204
                                                                  0000 FEET  DEPTH  CLASS 00
00625
TOT KJEL
N
MG/L

00610
NH3-N
TOTAL
MG/L
0.170
00671
PHOS-DIS
ORTHO
MG/L P
0.970
00665
PHOS-TOT
MG/L P
1.176
50051
FLOW
RATE
INST MGD

50053
CONDUIT
FLOX-MGD
MONTHLY


-------