U.S. ENVIRONMENTAL PROTECTION AGENCY
                NATIONAL EUTROPHICATION  SURVEY
                         WORKING PAPER SERIES
                                                REPORT
                                                  ON
                                           PALESTINE RESERVOIR
                                    ANDERSON, CHEROKEE, HENDERSON, AND
                                             SMITH COUNTIES
                                                TEXAS
                                             EPA REGION VI
                                          WORKING PAPER No, 654
     CORVALLIS ENVIRONMENTAL RESEARCH LABORATORY - CORVALLIS, OREGON
                                  and
    ENVIRONMENTAL MONITORING & SUPPORT LABORATORY - LAS VEGAS, NEVADA
•&G.P.O. 699-440

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                             REPORT
                               ON
                      PALESTINE RESERVOIR
              ANDERSON, CHEROKEE, HENDERSON, AND
                         SMITH COUNTIES
                             TEXAS
                         EPA REGION VI
                     WORKING PAPER No, 654
WITH THE COOPERATION OF THE
 TEXAS WATER QUALITY BOARD
           AND THE
    TEXAS NATIONAL GUARD
         APRIL, 1977

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                               CONTENTS
                                                           Page
  Foreward                                                   ii
  List of Texas Study Reservoirs                             iv
  Lake and Drainage Area Map                                 vi

  Sections
  I.  Conclusions                                             1
 II.  Lake and Drainage Basin Characteristics                4
III.  Lake Water Quality Summary                             5
 IV.  Nutrient Loadings                                      11
  V.  Literature Reviewed                                    16
 VI.  Appendices                                             17

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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)], clean lakes [§314(a,b)j,
and water quality monitoring [§106 and §305(b)] activities mandated
by the Federal Water Pollution Control Act Amendments of 1972.

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

ACKNOWLEDGEMENT

     The staff of the National Eutrophication Survey (Office of
Research & Development, U. S. Environmental  Protection Agency)
expresses sincere appreciation to the Texas  Water Quality Board
for professional involvement, to the Texas National Guard for
conducting the tributary sampling phase of the Survey, and to
those Texas wastewater treatment plant operators who voluntarily
provided effluent samples.

     Hugh C. Yantis, Jr., Executive Director of the Texas Water
Quality Board, and John B. Latchford, Jr., Director, and the staff
of the Field Operations Division provided invaluable lake documen-
tation and counsel  during the Survey, reviewed the preliminary
reports, and provided critiques most useful  in the preparation of
this Working Paper series.

     Major General  Thomas Bishop, the Adjutant General of Texas,
and Project Officer Colonel William L. Seals, who directed the
volunteer efforts of the Texas 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 Texas
NAME
Amistad
Bastrop
Bel ton
Braunig
Brownwood
Buchanan
Gaddo

Calaveras
Canyon
Colorado City
Corpus Christi
Diversion
Eagle Mountain
Fort Phantom Hill
Houston
Kemp
Lake O'The Pines

Lavon
Lewisville (Garza-Little Elm)
Livingston
COUNTY
Val Verde
Bastrop
Bell, Coryell
Bexar
Brown
Burnet, Llano
Harrison, Marion, TX;
Caddo Parish,  LA
Bexar
Comal
Mitchell
Jim Wells, Live Oak, San
Patricio
Archer, Baylor
Tarrant, Wise
Jones
Harris
Baylor
Camp, Marion,  Morris,
Upshur
Coll in
Denton
Polk, San Jacinto, Trinity,
Walker

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Lyndon B.  Johnson

Medina

Meredith


0. C. Fisher (San Angelo)

Palestine


Possum Kingdom


Sam Rayburn



Somervi lie

E. V. Spence

Stamford

Still house Hollow

Tawakoni

Texoma


Travis

Trinidad

Twin Buttes

White River

Whitney

Wright Patman (Texarkana)
Burnet, Llano

Bandera, Medina

Hutchinson, Moore,
Potter

Tom Green

Anderson, Cherokee,
Henderson, Smith

Palo Pinto, Stephens,
Young

Angelina, Jasper
Nacogdoches, Sabine, San
Augustine

Burleson, Lee, Washington

Coke

Haskell

Bell

Hunt, Rains, Van Zandt

Cooke, Grayson TX; Bryan,
Johnston, Love, Marshall, OK

Burnet, Travis

Henderson

Tom Green

Crosby

Bosque, Hill

Bowie, Cass

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Map Location
                  Flat Creek
                    Reservoir,
    PALESTINE RESERVOIR
        Sewage Treatment Facility
        Tributary Sampling Site
      X Lake Sampling Site
                                                   PALESTINE
                                                      RESERVOIR
^ Land Subject to Inundation

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                           PALESTINE RESERVOIR
                             STORE! NO. 4824

I.  CONCLUSIONS
    A.  Trophic Condition:
            Survey data indicate that. Palestine Reservoir is eutrophic;
        i.e., well supplied with nutrients and quite productive.
        Whether nutrient enrichment is beneficial or deleterious de-
        pends on the actual or potential effect on the uses of the
        reservoir.  In this regard, no nuisance conditions are known
        to personnel of the Texas Water Quality Board and there is
        little or no impairment of the designated beneficial uses of
        this water body.
            Palestine Reservoir ranked twenty-first in overall trophic
        quality when the 39 Texas reservoirs sampled in 1974 were com-
        pared using a combination of six parameters*.  Seventeen of the
        reservoirs had less and one had the same median total phosphorus,
        18 had less and one had the same median dissolved phosphorus,
        26 had less and one had the same median inorganic nitrogen, 18
        had less mean chlorophyll a^, and 14 had greater mean Secchi disc
        transparency.  Marked depression of hypolimnetic dissolved
        oxygen occurred at stations 1  and 2 in August.
* See Appendix A.

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        Survey limnologists noted surface algal  mats  at  station 4
    in May.  Previous investigators have noted  that the  upper
    portions of this water body are covered with dense growths of
    aquatic vegetation (Smith, 1974).
B.  Rate-Limiting Nutrient:
        The algal assay results indicate that Palestine  Reservoir
    was limited by phosphorus at the time the sample  was taken
    (03/19/74).  The reservoir data indicate phosphorus  limitation
    at three of the four stations in March, at  two stations  in May,
    and at two stations in November.
C.  Nutrient Controllability:
        1.  Point sources—During the sampling  year,  point  sources
    contributed 65.7% of the total phosphorus input to Palestine
    Reservoir.  The Tyler North Plant contributed an  estimated 58.6%
    of this total.
        The present phosphorus loading of 0.67  g/m2/year is  nearly
    1.8 times that proposed by Vollenweider (Vollenweider and Dillon,
    1974) as a eutrophic loading (see page 15).   Because most of  the
    reservoir is phosphorus limited, all point-source loads  should  be
    minimized to the greatest practicable extent. A  75% phosphorus
    reduction at the Tyler North Plant would reduce the  present load-
    ing to 0.38 g/m2/year and, if Vollenweider1s eutrophic  level  is
    applicable to Texas reservoirs, should result in  an  improved

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trophic condition in the reservoir once a new phosphorus equi-
librium has been established.
    2.  Non-point sources--Non-point sources contributed an
estimated 34.3% of the total phosphorus load during the sampling
year.  After point sources were subtracted, the Neches River
contributed 6.1% and Kickapoo Creek contributed 9.7%.  Other
gaged tributaries included Flat and Indian creeks which con-
tributed 2.9% and 0.9% of the total, respectively.  Ungaged
tributaries and immediate drainage contributed an estimated 12.1%
of the total.

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II.   RESERVOIR AND DRAINAGE BASIN CHARACTERISTICS1"

     A.   Morphometry  :

         1.   Surface area:   103.44 kilometers2.

         2.   Mean depth:   4.9 meters.

         3.   Maximum depth:  15.2 meters.

         4.   Volume:  508.001  x 106 m3.

         5.   Mean hydraulic retention  time:   1.3 years  (based on outflow),

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

         1.   Tributaries -

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

             Neches River                         564.6          2.082
             Flat Creek                           170.9          1.150
             Kickapoo Creek                       600.9          3.730
             Indian Creek                           60.1          0.404
             Minor tributaries &
              immediate drainage -                701.6          5.250

                              Totals            2,098.1         12.616

         2.   Outlet -

             Neches River                       2,201.5**       12.080

     C.   Precipitation***:

         1.   Year of sampling:   120.8  centimeters.

         2.   Mean annual:  117.4 centimeters.
 t Table of metric conversions—Appendix B.
 tt Latchford, 1974.
 * 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
      Palestine Reservoir was  sampled  four times  in  1974  by means of a
  pontoon-equipped Huey helicopter.  Each  time, samples for physical
  and chemical  parameters were collected from  two  or more depths at
  four stations on the reservoir (see  map, page vi).   During each
  visit, a single depth-integrated  (4.6 m  or near  bottom  to surface)
  sample was composited from the stations  for  phytoplankton identifi-
  cation and enumeration; and  during the March 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
  12.8 meters at station 1,  11.6 meters at station 2,  7.6 meters at
  station 3, and 3.4 meters  at station 4.
      The sampling results are presented in full  in  Appendix D  and are
  summarized in the following  table  (the August nutrient  samples were
  not properly  preserved and were not  analyzed).

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PARAMETER


TEMP 


DISS OXY (MG/L)


CNOCTVY  dlCROMO)


PH (STAND UNITS)


TOT ALK  (MG/U


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/L)


SECCHI  (METERS)
                             A. SUMMARY or PHYSICAL AND



                             1ST SAMPLING ( 3/ 9/74)


                                   4 SITES
                                  CHEMICAL CHARACTERISTICS FO* PALESTINE LAKE
                                   STGRET CODE 4324
     RANGE


 13.4  -  18.5


  7.7  -   9.4


 100.  -  160.


  6.9  -   7.5


  14.  -   23.


0.021  - 0.033


0.006  - 0.012


0.020  - 0.1/0


0.020  - 0.060


0.500  - 0.700


0,040  - 0.230


0.590  - 0.850


  3.1  -   4.5


  1.5  -   1.8
MEAN
16.1
8.7
120.
7.2
19.
0.025
0.009
0.119
0*035
0.573
0.154
0.693
3.8
1.7
MEDIAN
16.2
8.6
115.
7.2
21.
0.023
0.009
0.140
0.030
0.600
0.170
0.670
3.8
1.8
MEAN
24.1
5.0
167.
6.9
25.
MEDIAN
24.7
5.5
162.
6.9
24.
       2ND SAMPLING (  5/17/74)


             4 SITES


     RANGE


 19.1  -  26.4


  1.2  -   7.2


 141.  -  211.


  6.5  -   7.5


  23.  -   31.


0.023  - 0.054   0.038   0.033


0.007  - 0.026   0.013   0.010


0.020  - 0.170   0.057   0.050


0.030  - 0.210   0.113   0.115


0.500  - 1.000   0.637   0.600


0.050  - 0.380   0.170   0.170


0.540  - 1.020   0.694   0.685


  1.7  -  19.3     7.5     t.b


  0.9  -   1.4     1.2     1.3
        3RD SAMPLING ( 8/13/74)


              4 SITES


      RANGE        MEAN   MEDIAN


  22.9  -  28.9    27.1    27.0


   0.2  -   8,6     4.9     <*.6


  195.  -  221.    204.    204.


   7.3  -   8.6     7.8     7.6


0*0000  -OOOOOOOOOOOOOOOOOOOOOO


oooooo  .oooooooooooooooooooooo


oooooo  -ooooooooooeooooooooooo


oooooo  -oooooooooooooooooooooo


oooooo  .0000000000000000000000


oooooo  -oooooooooooooooooooooo


oooooo  -oooooooooooooooooooooo


oooooo  -oooooooooooooooooooooo



   2.6  -  34.5    24*9    31.2


   1.2  -   1.8     1.5     1.5

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                              A.  SUMMARY  OF  PHYSICAL AND CHEMICAL CHARACTERISTICS FOR PALESTINE LAKE
                                                          STORET COU£
PARAMETER

TEMP (C)

DISS OXY (MG/L)

CNOCTVY (MCROMO)

PH (STAND UNITS)

TOT ALK (MG/L)

TOT P (MG/U)

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 
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B.  Biological characteristics:

    1.   Phytoplankton -
        Sampling
        Date

        03/09/74
        05/17/74
        08/13/74,
        11/01/74
Dominant
Genera
1.
2.
3.
4-..
5.
1.
2.
3.
4.,
5,,
1,
2.
3.
4.
5.
1.
2.
3.
4,
5..
Melosira sp.
Chroomonas sp.
Cryptomona.s sp_.
Microcystis sp.
Ankistrodesmus sp.
Other genera-

        Total

Melosira sp.
Chroomonas S£.
Dactylococcopsis sp.
Microcystis sp.
Cruc.igenia sp.
Other genera

        Total

Dactyloco.ccopsi s sp.
Melosira sp.
C'ryptomonas sp.
Pennate diatoms
Raphidiopsis sp.
Other genera

        Total

MeTosira s£.
Dactylococcopsis sp.
Coccoid ce.lls
Nitz.s.chia sp.
Microcystis sp.
Other genera
Alqal Units
per ml'	

    1,452
      881
      674
      441
      285
      907

    4,640

    1,032
      534
      138
      138
      120
      688
                                                              2,650
                                                              5,102
                                           Total
                                1,647

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    2.   Chlorophyll  a -
        Sampling
        Date

        03/09/74
        05/17/74
        08/13/74
        11/01/74
Station
Number

   1
   2
   3
   4

   1
   2
   3
   4

   1
   2
   3
   4

   1
   2
   3
   4
Chlorophyll  a_
C.   Limiting Nutrient Study:

    1.  Autoclaved, filtered,  and nutrient spiked -
                         Ortho P
                         Cone, (mg/1)
            Inorganic N
            Cone,  (mg/1)
     3.1
     3.4
     4.5
     4.3

     1.7
     4.5
     4.7
    19.3

     2.6
    34.5
    31.9
    30.5

     3.3
     5.1
     4.7
    11.8
Maximum yield
(mg/1-dry wt.)
Spike (mg/1)

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

            The control  yield of the assay alga,  Selenastrum  capri-

        cornutum,  indicates that the potential  primary productivity
0.005
0.055
0.055
0.005
0.183
0.183
1.183
1.183
1.9
5.6
20.6
2.3

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                        10
of Palestine Reservoir was moderately high at the time the
sample was collected (03/19/74).  Also,  a significant increase
in yield with the addition of phosphorus alone indicates  that
the reservoir was limited by phosphorus  at that time.   Note
that the addition of nitrogen alone resulted in a yield which
was not significantly greater than that  of the control.
    The reservoir data indicate phosphorus limitation in  March
(the mean inorganic nitrogen/orthophosphorus ratio was 17/1);
narrow nitrogen limitation in May (the mean inorganic
nitrogen/orthophosphorus ratio was 13/1); and phosphorus
limitation in November (the mean inorganic nitrogen/ortho-
phosphorus ratio was 14/1).
    The reservoir data indicate a spatial and temporal  com-
bination of limiting nutrients.  Following is a tabulation
of the mean inorganic nitrogen/orthophosphorus ratios for each
of the sampling station and times with the indicated  limiting
nutrient in parentheses.  Note that those stations nearest
nutrient point sources (e.g., station 4) tended toward
nitrogen limitation.
Station        03/09/74           05/17/74       11/01/74
   1           22/1 (P)           13/1 (N?)      24/1  (P)
   2           17/1 (P)           17/1 (P)       18/1  (P)
   3           15/1 (P)           16/1 (P)       12/1  (N)
   4            5/1 (N)            6/1 (N)        5/1  (N)

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                                     11
IV.   NUTRIENT LOADINGS
     (See Appendix E  for data)
     For the determination  of nutrient  loadings,  the Texas National
 Guard collected monthly near-surface grab  samples  from each of the
 tributary sites indicated  on the  map (page vi),  except for the months
 of April and May when  two  samples were collected.  Sampling was begun
 in September, 1974,  and was  completed  in August, 1975.
     Through an interagency agreement,  stream  flow  estimates for the
 year of sampling and a "normalized" or average year were provided by
 the Texas 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" ("II" of U.S.G.S.) were estimated using  the nutrient loads
 at station B-l, in kg/km2/year, and multiplying  by the II area in km2.
     The operators of the Brownsboro, Tyler, Henderson County Municipal
 Water Supply, and Van  wastewater  treatment plants  did not participate
 in  the Survey;  nutrient loads from these sources were estimated at
 1.134 kg P and  3.401 kg N/capita/year,  and flows for the Brownsboro
 and Tyler North Plant  were estimated at 0.3785 m3/capita/day.
   See  Working  Paper No.  175.

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                                    12
    A.  Waste Sources:

        1.  Known municipal  -
        Name

        Brownsboro
        Tyler
         North plant
         Kelly
          Springfield
           Plant*
        Henderson Cty.
         Mun. Water
          Supply*
        Van*
Pop.
Served
36,000
 1,400
   500


 2,000
Treatment
   510    stab,  pond
tr.  fi1ter
contact
 stab.

contact
 stab.

contact
 stab.
Mean Flow
(m3/d)

    193.0

 13,626.0
    113.6*
    283.9*
  1,135.5*
Receiving
Water

Kickapoo Creek

Black Fork Creek*
Saline Creek
Unnamed Creek/
 Palestine Res.

Big Sandy Creek/
 Neches R.
t Anonymous, 1971.
* Wyatt, 1976.

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                                    13
    B.   Annual Total  Phosphorus Loading - Average Year:

        1.   Inputs -

                                              kg P/          % of
            Source                            yr             total

            a.  Tributaries (non-point load)  -

                Neches River                   4,235           6.1
                Flat  Creek                     2,005           2.9
                Kickapoo Creek                 6,735           9.7
                Indian Creek                     620           0.9

            b.  Minor tributaries & immediate
                 drainage (non-point load) -    8,420          12.1

            c.  Known municipal STP's -

                Brownsboro                       580           0.8
                Tyler
                 North plant                  40,825          58.6
                 Kelly Springfield plant       1,590           2.3
                Henderson Cty. Mun. Water
                 Supply                          565           0.8
                Van                            2,270           3.2

            d.  Septic tanks - Unknown           ?

            e.  Known industrial - None

            f.  Direct precipitation* -        1.810           2.6

                        Total                  69,655         100.0

        2.   Outputs -

            Lake outlet - Neches River         8,995

        3.   Net annual P accumulation - 60,660 kg.
* See Working Paper No. 175.

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                                    14
    C.  Annual Total Nitrogen Loading - Average Year:

        1.  Inputs -

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

                Neches River                   49,590          9.2
                Flat Creek                     27,335          5.0
                Kickapoo Creek                 96,430         17.8
                Indian Creek                    6,845          1.3

            b.  Minor tributaries & immediate
                 drainage (non-point load) -   112,255         20.7

            c.  Known municipal STP's -

                Brownsboro                      1,735          0.3
                Tyler
                 North plant                  122,435         22.6
                 Kelly Springfield plant        4,760          0.9
                Henderson Cty. Mun. Water
                 Supply                         1,700          0.3
                Van                             6,800          1.3

            d.  Septic tanks - Unknown            ?

            e.  Known industrial - None

            f.  Direct precipitation* -       111,675         20.6

                        Total                  541,560        100.0

        2.  Outputs -

            Lake outlet - Neches River        231,505

        3.  Net annual N accumulation - 310,055 kg.

    D.  Non-point Nutrient Export by Subdrainage Area:

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

        Neches River                               8             88
        Flat Creek                                12             160
        Kickapoo Creek                            11             160
        Indian Creek                              10             114
* See Working Paper No. 175.

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                                15
E.   Mean Nutrient Concentrations in Ungaged Streams:
                                          Mean Total  P   Mean  Total  N
    Tributary                             Cone,  (mg/1)   Cone,  (mg/1)
    Butler Creek                              0.036          0.678
    Saline Creek                              0.050          0.968
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/mVyr             0.67       0.59        5.24        3.00
    Vollenweider phosphorus loadings
     (g/m2/yr) based on mean depth and mean
     hydraulic retention time of Palestine Reservoir:
        "Dangerous"  (eutrophic loading)             0.38
        "Permissible"  (oligotrophic loading)        0.19

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                                    16
V.  LITERATURE REVIEWED

    Anonymous, 1971.  Inventory of municipal  waste facilities.   EPA  Pub.
        No. OWP-1, vol. 6, Wash., DC.

    Latchford, John B. Jr., 1974.  Personal  communication  (morphometry).
        TX Water Qual. Bd., Austin.

    Smith, Stephen F., 1974.  Fishery management recommendations.  Fed.
        Aid Proj. F-25-R-3, TX Parks & Wildlife Dept.,  Austin.

    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.

    Wyatt, Linda B., 1976.  Personal communication (discharge points of
        Tyler STPs).  TX Water Qual. Bd., Austin.

-------
                                 17
VI.  APPENDICES
                                  APPENDIX A
                                 LAKE RANKINGS

-------
LAKE. DATA TO 8E USED IN SINKINGS
LAKE
CODE  LAKE NAME
4801  AMISTAD LAKE
4802  BASTROP LAKE
4803  SELTON RESERVOIR
4804  BRAUNIG LAKE
4805  BRO*NWOOD LAKE
4806  LAKE BUCHANAN
4807  CADOO LAKE
4808  CALAVERAS LAKE
4809  CANYON RESERVOIR
4810  LAKE COLORADO CITY
4811  CORPUS CRISTI LAKE
4812  DIVERSION LAKE
4813  EAGLE MOUNTAIN LAKE
4814  FT PHANTOM HILL LAKE
4815  GARZA LITTLE ELM RESEWVO
4816  KEMP LAKE
4817  HOUSTON LAKE
4818  LAKE OF THE PINES
4819  LAVON RESERVOIR
4820  LIVINGSTON LAKE
4821  LYNDON B JOHNSON LAKE
4822  MEDINA LAKE
4823  LAKE MEREDITH
4824  PALESTINE LAKE
4825  POSSUM KINGDOM RESERVOIR
4826  SAN ANGELO RESERVOIR
482?  SAM RAYBURN RESERVOIR
4828  E V SPENCE RESERVOIR
MEDIAN
TOTAL P
0.013
0:02?
0.016
0.134
0.027
0.036
0.055
0.038
0.010
0.042
0.113
0.025
0.024
0.060
0.045
0.023
0.097
0.031
0.063
0.196
0.042
0.010
0.021
0.031
0.023
0.098
0.029
0.036
MEDIAN
INOPG N
0.500
0.090
0.165
0.150
0.100
0.250
0.070
0.060
0.450
0.090
0.130
0.080
0.070
0.105
0.380
0.110
0.260
0.090
0.180
0.555
0.420
0.600
0.070
0.180
0.070
0.140
0.150
0.080
500-
MEAN SEC
371.f74
419.917
378.312
461.625
470.375
437.625
463.333
461.667
384.612
473.625
475.187
470.111
469.625
474.909
475.782
455.000
486.187
440.000
485.333
465.469
456.500
403.562
439.312
442.625
419.045
481.000
439.458
462.583
MEAN
CHLORA
2.042
12.392
6.025
22.762
4.887
8.606
14.808
22.500
2.500
12.675
19.756
15.867
5.662
6.317
14.156
10.217
16.650
12,919
5.400
16.112
8.100
12.944
3.037
10.619
9.495
24.675
6.267
11.775
15-
MIN oo
14.900
15.000
15.000
14.800
14.400
15.000
11.400
13.000
14.800
10.200
14.000
9.000
11.000
9. BOO
14.600
10.400
12.400
15.000
8.800
15.000
14.900
15.000
14.^00
14.800
15.000
10.200
15.000
15.000
MEDIAN
OISS O^TriO P
0.009
0.007
0.007
0.062
0.007
0.012
0.013
0.007
0.006
0.012
0.050
0.009
0.008
0.022
0.018
0.007
0.036
0.011
0.018
0.128
0.013
0.004
0.009
0.010
0.009
0.011
0.009
0.008

-------
LAKE DATA TO BE USED IN RANKINGS


LAKE
CODE  LAKE NAME

4829  SOMERVILLE LAKE

4830  STAMFORD LAKE

4631  STILLHOUSE HOLLOW RESEHV

4832  TAWAKONI LAKE

4833  TEXARKANA LAKE

4834  TEXOMA LAKE

4835  TRAVIS LAKE

4836  TRINIDAD

4837  TWIN  8UTTES RESERVOIR

4838  WHITE RIVER RESERVOIR

4839  WHITNEY  LAKE
MEDIAN
TOTAL P
0.053
0.073
O.Olb
0.046
O.lOb
0.042
0.018
0.389
0.029
0.020
0.028
MEDIAN
1NORG N
0.115
0.060
0.160
0.100
0.120
0.160
0.250
0.110
0.250
0.110
0.120
500-
MEAN SEC
473.033
482.714
406.250
466.417
478.500
451.321
389.913
479.500
454.917
434.500
430.500
MEAN
CHLOSA
24.^91
18.457
3.917
18.246
19.119
12.493
5.595
24.300
8.708
4.333
6.912
15-
MIN 00
13.000
10.600
15.000
13.200
12.400
15.000
15.000
10.000
14.800
15.000
15.000
MEOIAN
DISS GrfTriO if>
0.01 J
0.012
0.010
0.013
0.030
0.018
0.007
0.240
0.009
0.009
0.008

-------
LAKCS RANKED BY INDEX NOS,
RANK  LAKE CODE  LAKE NAME
                                       INDEX NO
 i  4809       CANI-ON RESERVOIR           445
 2  4823       LAKE MEREDITH              ^41
 3  4813       EAGLE MOUNTAIN LAKE        430
 4  4816       KEMP LAKE                  423
 5  4801       AMISTAO LAKE               402
 6  4805       BROaNWOOD LAKE             394
 7  4802       BASTRuP LAKE               393
 8  4838       WHITE RIVER RESERVOIR      390
 9  4825       POSSUM KINGDOM RESERVOIR   387
10  4835       TRAVIS LAKE                384
11  4803       BELTON RESERVOIR           384
12  4831       STILLHOUSE HOLLOW PESERV   372
13  4812       DIVERSION LAKE             372
14  4808       CALAVERAS LAKE             362
15  4839       WHITNEY LAKE               357
16  4822       MEDINA LAKE                342
17  4827       SAM RAYBURN RESERVOIR      322
18  4828       E V SPENCE RESERVOIR       321
19  4837       Twin BUTTES RESERVOIR      311
20  4810       LAKE COLORADO CITY         310
21  4824       PALESTINE LAKE             302
22  4818       LAKE OF THE PINES          298
23  4807       CADDO LAKE                 297
24  4814       FT PHANTOM HILL LAKE       296
25  4806       LAKE BUCHANAN              261
26  4830       STAMFORD LAKE              259
27  4819       LAVON RESERVOIR            258
28  4832       TAWAKOM LAKE              253

-------
LAKES RANKED BY INDEX NOS.
RANK  LAKE CODE  LAKE NAME               INOEX NO
  29  4821       LYNDON 8 JOHNSON LAKE      238
  30  4834       TEXOMA LAKE                217
  31  4829       SOMERVILLE LAKE            208
  32  4826       SAN ANGELO RESERVOIR       200
  33  4833       TEXARKANA LAKE             176
  34  4815       GARZA LITTLE ELM RESERvO   173
  35  4836       TRINIDAD                   169
  36  4804       BRAUNIG LAKE               159
  37  4811       CORPUS CRIST I LAKE         155
  38  4817       HOUSTON LAKE               139
  39  4820       LIVINGSTON LAKE             91

-------
PERCENT OF LAKES t(ITM HlGHtR VALUES (NUMBER OF LAKES wiTH HlGHE* VALUES)
LAKE
CODE  LAKE NAME
4801  AMISTAD LAKE
4B02  HASTROP LAKE
4803  BELTON RESERVOIR
4804  BRAUNIG LAKE
4805  BROrfNWOOD LAKE
4806  LAKE BUCHANAN
4807  CADDO LAKE
4808  CALAVERAS LAKE
4809  CANYON RESERVOIR
4810  LAKE COLORADO CITY
4811  CORPUS CRIST I LAKE
4812  DIVERSION LAKE
4813  EAGLE MOUNTAIN LAKE
4814  FT PHANTOM HILL LAKE
4815  GARZA LITTLE ELM RESERVO
4816  KEMP LAKE
4817  HOUSTON LAKE
4818  LAKE OF THE PINES
4819  LAVON RESERVOIR
4820  LIVINGSTON LAKE
4821  LYNDON B JOHNSON LAKE
4822  MEDINA LAKE
4823  LAKE MEREDITH
4824  PALESTINE LAKE
4825  POSSUM KINGDOM RESERVOIR
4826  SAN ANOELO RESERVOIR
4827  SAM RAYBURN RESERVOIR
4828  E V SPENCE RESERVOIR
MEDIAN
TOTAL P
95
79
92
5
66
47
26
45
99
39
8
68
71
24
34
76
16
54
21
3
39
99
82
54
74
13
59
50
( 36)
( 30)
< 35)
( 2)
( 25)
( 18)
( 10)
( 17)
( 37)
( 14)
( 3)
( 26)
( 27)
( 9)
( 13)
( 29)
( 6)
( 20)
( 8)
( 1)
( 14)
( 37)
( 3D
( 20)
( 28)
( 5)
( 22)
( 19)
MEDIAN
INORG N
5
76
26
42
70
21
91
100
8
76
47
83
91
66
13
61
16
76
29
3
11
0
91
32
91
45
39
83
( 2)
( 28)
( 10)
( 16)
( 26)
( 7)
( 33)
< 38)
( 3)
( 28)
( 18)
( 31)
( 33)
( 25)
( 5)
( 22)
< 6)
( 28)
( 11)
( 1)
( 4)
( 0)
( 33)
( 12)
( 33)
( 17)
( 15)
( 31)
500-
MEAN SEC
100
b2
97
50
29
74
42
47
95
26
18
32
34
21
16
55
0
66
3
39
53
89
71
63
84
8
68
45
( 38)
( 3D
( 37)
( 19)
( 11)
( 28)
( 16)
( 18)
( 36)
( 10)
( 7)
( 12)
( 13)
( 8)
( 6)
< 21)
( 0)
( 25)
< 1)
( 15)
( 20)
( 34)
< 27)
( 24)
( 32)
( 3)
f 26)
( 17)
MEAN
CHLOHA
100
47
68
8
87
63
32
11
97
42
13
29
79
74
34
55
24
39
84
26
66
37
95
53
53
0
76
50
( 38)
( 18)
< 26)
( 3)
( 33)
( 24)
( 12)
( 4)
< 37)
( 16)
( 5)
( 11)
( 30)
( 28)
< 13)
( 21)
( 9)
( 15)
( 32)
( 10)
( 25)
( 14)
( 36)
( 20)
( 22)
( 0)
( 29)
( 19)
15-
MIN UO
39 (
17 (
17 (
49 (
58 <
17 (
76 <
67 (
49 (
88 (
61 (
97 (
79 <
95 (
55 (
84 (
72 (
17 (
100 (
17 (
39 (
17 (
39 (
49 (
17 (
88 (
17 (
17 (
14)
0)
0)
17)
22)
0)
29)
25)
17)
33)
23)
37)
30)
36)
21)
32)
27)
0)
38)
0)
14)
0>
14)
17)
0)
33)
0)
0)
MEDIAN
DISS OWTHO P
63
92
84
5
84
39
30
92
97
39
8
63
76
16
21
92
11
46
21
3
30
100
63
51
63
46
63
76
( 21)
( 34)
( 3D
( 2)
( 3D
( 14)
( 10)
( 34)
( 37)
( 14)
( 3)
( 21)
( 28)
( 6)
( 7)
( 34)
( 4)
( 17)
( 7)
( 1)
( 10)
( 38)
( 21)
( 19)
( 21)
( 17)
( 21)
( 28)
INDEX
NO
402
3-n
364
159
394
261
297
362
445
310
155
372
430
296
173
423
139
298
258
91
238
342
441
302
367
200
322
321

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

LAKE
CODE  LAKE NAME

4829  SOMERVILLE LAKE

4830  STAMFORD LAKE

4831  STILLHOUSE HOLLOW REStXV

4832  TAWAKONI LAKE

4833  TEXARKANA LAKE

4834  TEXOMA LAKE

4835  TRAVIS LAKE

4836  TKINIOAD

4837  TWIN BUTTES RESERVOIR

4838  WHITE RIVER RESERVOIR

4839  WHITNEY LAKE
MEDIAN
TOTAL P
21 (
18 (
88 (
32 (
11 (
39 <
88 (
0 (
59 (
84 (
63 (
11)
7)
33)
12)
4)
14)
33)
0)
22)
32)
34)
MEDIAN
INORG N
55
97
37
70
51
34
21
61
21
61
51
( 21)
( 37)
( 14)
( 26)
( 19)
( 13)
( 7)
( 22)
( 7)
< 22)
( 19)
500-
MEAN SEC
24 (
5 (
67 (
37 (
13 (
61 (
92 (
11 (
58 (
76 (
79 (
9)
2)
33)
14)
5)
23)
35)
4)
22)
29)
30)
MEAN
CHLORA
3
18
92
21
16
45
82
5
61
89
71
( 1)
( 7)
( 35)
( 8)
( 6)
< 17)
( 3D
( 2)
( 23)
( 34)
( 27)
15-
MIN DO
67
82
17
63
72
17
17
92
49
17
17
( 25)
( 3D
( 0)
( 24)
( 27)
( 0)
( 0)
( 35)
( 17)
( 0)
( 0)
MEDIAN
Diss U^THO P
30
39
51
30
13
21
84
0
63
63
76
( 10)
( 14)
( 19)
I 10)
( 5)
( 7)
( 3D
( 0)
( 21)
( 21)
( 28)
INDEX
NO
208
259
372
253
176
217
J84
169
311
390
357

-------
    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
  f
Kilograms x 2.205 = pounds

Kilograms/square kilometer x 5.711 = Ibs/square mile

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

-------
                                   TRIBUTARY PLOW INFORMATION FOR T£XA5
                                                                       04/14/76
LANE CODE 48?4
PALESTINE RESERVOIR
     TOT-AL DRAINAGE AREA OF LAKE'SQ KM)   3201.5
          SUB-DRAINAGE
TRIBUTARY  AREAfSQ KM)
       JAN
FEB
MAR
              NORMALIZED FLOrfS(CMS)
APR     MAr     JUN     JUL     AUG
                                                                               OCT
                                                                                                           NOV
                                                                                DtC
                                                                                                                          MEAN
4824A1
482-+A2
4824ril
482-«Cl
4824D1
4824ZZ
2201.5
564.6
170.9
600.9
60.1
805.5
10.87
0.363
1.02
3.77
0.453
5.13
12.94
0.566
1.10
4.70
0.481
5.97
20.47
0.311
0.71
6.40
0.255
5.49
29.17
1.341
2.75
9.51
0.934
10.70
30.87
2.520
2.78
8.27
0.934
12.03
15.29
6.230
1.10
4.02
0.340
5.97
3.40
0.068
0.57
0.34
0.170
1.53
1.67
2.152
0.28
0.23
0.085
1.19
4.05
4.078
0.71
0.42
0.255
2.80
2.01
0.425
0.93
1.39
0.340
3.26
5.75
5.947
0.96
1.7B
0.3^0
4.56
8.75
0.651
0.88
4.08
0.275
4.56
12.08
2.082
1.15
3.73
0.404
5.25
                                                                   SUMMARY
                        TOTAL DRAINAGE AREA OF LAKE =    2201.5
                        SUM OF SUB-DRAINAGE AREAS   =    2202.0
                                                           TOTAL FLO* IN  =    151.93
                                                           TOTAL FLO* OUT =    145.24
     MEAN MONTHLY FLOWS AND DAILY FLOWS(CMS)
TRIBUTARY   MONTH   YEAR
4824A1
         MEAN FLOW  DAY
                 FLOW  DAY
                           FLOW  DAY
                                     FLOW
4824A2

-------
                                   TRIBUTARY FLOw INFORMATION FOR TEXAS
                                                                                          04/14/76
     CODE 4824
                   PALESTINE RESERVOIR
     MEAN MONTHLY FLOWS AND DAILY FLOWS(CMS)
TRIBUTARY   MONTH   YEAri
4624^1
4824CI
 4824D1
 4824ZZ
9
10
11
12
1
2
3
4
5
6
7
8
9
10
11
12
1
2
3
4
5
6
7
8
9
10
11
12
1
2
3
4
5
6
7
8
9
10
11
12
1
2
3
4
S
6
7
8
74
74
74
74
75
75
75
75
75
75
75
75
74
74
74
74
75
75
75
75
75
75
75
75
74
74
74
74
75
75
75
75
75
75
75
75
74
74
74
74
75
75
75
75
75
75
75
75
                            MEAN FLOW  DAY
                                                   FLO*  DAY
                                                                     FLOW  DAY
                                                                                       FLOW
0.595
0.311
4.729
2.492
1.926
3.313
1.982
2.379
3.596
1.076
0.082
0.028
2.095
1.1C4
16.849
8.920
6.853
11.836
7.108
8.580
12.884
3.794
0.283
0.040
0.210
0.110
1.699
0.906
0.680
1.189
0.708
0.850
1.303
0.368
0.028
0.085
15.008
12.743
11.044
10.760
11.638
25.315
9.401
9.571
26.193
19.482
1.161
0.793
7
14
23
30
26
23
23
6
4
6
19
17
7
14
23
30
26
23
23
6
4
6
19
17
7
14
22
30
25
22
22
6
3
6
19
17












0.119
0.150
0.566
2.322
0.821
0.878
1.954
0.595 IB
5.097 16
0.481
0.051
0.003
0.425
0.538
2.039
8.325
2.917
3.171
7.023
2.095 18
18.179 16
1.784
0.184
0.011
0.042
0.054
0.218
0.821
0.283
0.34U
0.906
0.210 Ib
2.888 16
0.178
0.017
0.001



















3.3^3
1.303










12.120
4.644










1.218
0.453
















-------
        APPENDIX D





PHYSICAL and CHEMICAL DATA

-------
 48?401
32 03 15.0 095 26 16.0
PALESTINE LAKE
48001   TEXAS
DATE
FROM
TO
74/03/09


74/05/17



74/08/13




74/11/01



DATE
FROM
TO
74/03/09





74/05/17






74/08/13

74/11/01




TIME
OF
DAY
12
12
12
12
12
12
10
10
10
10
10
10
10
10
10
10
15
15
15
15
15

40
40
40
40
40
48
40
40
40
40
40
40
40
40
40
40
00
00
00
00
00

TIME
OF
DAY
12
12
12
12
12
12
10
10
10
10
10
10
10
10
10
15
15
15
15
15


40
40
40
40
40
48
40
40
40
40
40
40
40
40
40
00
00
00
00
00
DEPTH
FEET
0000
0006
0015
0025
0040
0000
0000
0005
0015
0030
0040
0000
0005
0015
0025
0042
0000
0005
0015
0027
0041

DEPTH

FEET
0000
0006
0015
0025
0040
0000
0000
0001
0005
0006
0015
0030
0040
0000
0007
0000
0005
0015
0027
0041
OC010
WATER
TEMP
CENT
15. 8
15.6
15.1
15.0
13,4
23.2
23.0
22.5
21.0
19.1
27.0
26.9
26.8
26.8
22,9
22.6
22.3
22.3
22.1
22.0
00665
PHOS-TOT

MG/L P

0.022
0.021
0.021
0.021
0.023
0.036

0.033

0.043
fc . 0 5<»
0.046


0.031
0.029
0.028
0.032
.,0.037
00300 00077 00094
DO TRANSP CNOUCTVY
SECCHI FIELO
MG/L INCHES MICROMHO
72
9.1
8.8
8.8
8.2
55
5.0
3.2
2.8
1.2
54
4.6
4.0
4.0
0.2
6.4 47
7.6
6.6
6.0
5.6
32217 00031
CHLRPHYL INCDT LT
A HEMMING
UG/L PERCENT
3.1





1.7
50,0

1.0



2.6
1.0
3.3




108
111
105
100
102
152
152
148
142
141
196
196
195
196
218
141
146
147
147
144
























llEPALtS 2111202
4 0044 FEET Q£MTri
00400 00410 00610 00625 00630 00671
pH T ALK NH3-N TOT KJEL N02&N03 PHOS-OIS
CAC03 TOTAL N N-TOTAL ORTriO
SU MG/L MG/L MG/L MG/L MG/L P
7.50
7.40
7.30
7.05
7.10
7.10
7.00
6.60
6.50
6.50
7.80
7.80
7.60
7.50
7.35
6.63
6.65
6.64
6.58
6.58

























20 0.020
20 0.040
22 0.060
22 0.060
23 0.030
24 0.120
24 0.140
24 0.160
25 0.160
29 0.210





30 0.030
31 0.030
31 0.030
32 0.030
31 0.040

























0.500
0.500
0.500
0.500
0.700
0.700
0.500
0.500
0.700
0.600





0.600
0.400
0.400
0.400
0.400

























0.150
0.160
0.170
0.170
0.1SU
0.060
0.070
0.080
0.070
0.170





0.200
0.200
0.200
0.210
0.220

























0.008
0.006
0.012
0.009
0.010
0.020
0.017
0.018
0.018
0.026





0.007
0.011
0*009
0.010
0.012

























-------
STORET RETRIEVAL DATE  76/02/11
                                                                  482*02
                                                                 32 Ua 46.0 095 26 08.0
                                                                 PALESTINE LAKE
                                                                 48073   TEXAS
UEFALtS 2111202
<• 0034 FEET DEPTH
DATE
FROM
TO
74/03/0*
74/05/17
74/08/13




74/11/01
TIME
OF
DAY
13
13
13
13
11
11
11
11
11
11
11
11
11
14
14
14
14
20
20
20
20
05
05
05
05
15
15
15
15
15
35
35
35
35
DEPTH
FEET
0000
0006
0015
0030
0000
0005
0015
0032
0000
0005
0015
0025
0035
0000
0005
0015
0038
00010
WATER
TEMP
CENT






16.3
16.3
16.2
15.1
24.7
24.6
24.5
23.6
27.3
27.3
26.9
26.9
25.0
22.9
22.6
22.5
22.3
00665
DATE
FROM
TO
74/03/09



74/05/17





74/08/13

74/11/01



TIME
OF
DAY
13
13
13
13
1
1
1
1
1
11
11
11
14
14
14
14


20
20
20
20
05
05
05
05
05
05
15
15
35
35
^5
35
DEPTH

FEET
0000
0006
0015
0030
0000
0001
0005
0006
0015
0032
0000
0008
0000
0005
001S
0038
PHOS-TOT


MG/L P
0
0
0
0
0

0

0
0
.024
.022
.022
.026
.023

.029

.031
.034
00300 00077 00094
DO TrtAMSP CNDUCTVY
SECCHI FIELD
MG/L INCHES MICSOMHO
72
9.3
8.7
8.1
47
6.0
4.0
4.4
5.4 48
5.
4.
4.
0.
7.
6.
6.
6.
32217
6
6
0
2
2 60
8
6
8
00031
114
115
115
119
161
162
160
150
198
198
198
198
221
145
146
148
145

00400 00410 00610 00625 00630 00671
PH T ALK NH3-N TOT KJEL N02&.N03 PnOS-DIS
CAC03 TOTAL N N-TOTAL ORTr,o
SLI rt&'L Mt>/L MG/L MG/L MG/L P
7.
7.
7.
6.
6.
6.
6.
6.
7.
7.
7.
7.
7.
6.
6.
6.
6.

20
25
00
90
65
90
60
55
70
65
50
50
30
90
78
70
66

21 0.030 0.700 0.140 0.011
22 0.020 0.500 0.140 0.008
23 0.030 0.600 0.140 0.012
21 0.050 0.500 0.130 0.008
23 0.110 0.700 0.080 0.010
23 0.100 0.500 0.040 0.008
25 0.140 0.500 0.050 0.012
24 0.1<*0 0.500 0.050 0.012




35 0.040 0.600 0.170 0.015
35 0.030 0.500 0.180 0.013
34 0.040 0.500 0.180 0.010
32 0.060 0.600 0.160 0.010

CHLRPHYL INCDT LT
A
UG/L
3.



4.





tfEMNING
PERCENT
4



5
50.0

1.0


















































34.5

0
0
0
0

.046
.033
.031
.059

5.



1.0
1
























-------
STORET RETRIEVAL CATt 76/03/11
                                                                   482403
                                                                  32  06  40.0  095 2o  19.0
                                                                  PALESTINE LAKE
                                                                  4821J    TE*AS
  DATE   TIME DEPTH
  FROM    OF
   TO    DAY  FEET
74/03/09 14 00 0000
14 00 0006
14 00 0015
14 00 0021
74/05/17 1
1
1
1
74/08/13 1
1
1
1
1 25 0000
1 ?5 0005
1 25 0015
1 25 0021
1 45 0000
1 45 0005
1 45 0015
1 45 0020
74/11/01 14 15 0000
14 15 0005
14 15 0015
14 15 0025
 00010
WATER
 TEMP
 CENT

   16.3
   16.7
   16.4
   15.4
   25.2
   25.2
   25.0
   25.0
   28.4
   27.9
   27.1
   26.9
   22.8
   22.4
   22.3
   21.7
llEPiLtS

00300
00
MG/L

9.4
8.9
7.7

6.6
6.0
6.6
8.2
7.0
3.6
3.4
6.8
7.0
6.0
5.6

00077
TRANSP
SECCHI
INCHES
&9



54



72



60




00094
CNOUCTVY
FIELD
MICROMHO
123
128
128
134
168
168
166
165
204
204
204
204
147
146
145
142
4
00400
PH
su
7.40
7.40
7. 20
6.90
6.90
7.00
7.10
6.90
8.10
7.90
7.60
7.40
6.79
6.66
6.59
6.67
211
1202


0025 FEET DEPTH
00410
T ALK
CAC03
MG/L
21
15
15
15
24
24
24
23




37
36
43
42
00610
NHJ-N
TOTAL
MG/L
0.030
0.020
0.030
0.060
0.100
0.120
0.100
0.100




0.050
0.050
0.070
0.090
00625
TOT KJEL
N
MG/L
0.600
0.600
0.500
0.600
0. '00
0.600
0.600
0.600




0.200
0.200K
0.500
0.600
00630
N02&N03
N-TOTAL
MG/L
0. 120
0.100
0.090
0.080
0.040
0.040
0.050
0.050




0.120
0.110
0.110
0.110
00671
HHOS-G1S
ORTHO
MG/L P
0.00V
0.009
0.008
0.009
0.007
0.011
0.009
0.010




0.011
0.018
0.014
0.015
DATE
FROM
TO
74/03/09



74/05/17



74/08/13

74/11/01



00665 32217 00031
TIME DEPTH PHOS-TOT CHLRPHYL INCDT LT
OF A REMNING
DAY FEET
14
14
14
14
11
11
11
11
11
11
14
14
14
14
00
00
00
00
25
25
25
25
45
45
15
15
15
15
0000
0006
0015
0021
0000
0005
0015
0021
0000
0010
0000
0005
0015
0025
MG/L P UG/L PERCENT
0
0
0
0
0
0
0
0


0
0
0
0
.028 4.5
.027
.023
.027
.029 4.7
.031
.028
.028
31.9
1.0
.037 4.7
.038
.037
.047
           K VALUE KNOWN  TO  BE
           LESS THAN  INDICATED

-------
STORET RETRIEVAL DATE  76/03/11
32 U 40.0 OVS
PALESTINE
                                                                                    32.0
DATE
FROM
TO
74/03/09

74/05/17


74/08/13


74/11/01



DATE
FROM
TO
74/03/09

74/05/17


74/08/13
74/11/01


TIME DEPTH
OF
DAY FEET
14 30 0000
14 30 0006
11 45 0000
11 45 0005
11 45 0011
12 15 0000
12 15 0005
12 15 0009
13 55 0000
13 55 0005
13 55 0011

TIME DEPTH
OF
DAY FEET
14 30 0000
14 30 0006
11 45 0000
11 45 0005
11 45 0911
12 15 0000
13 55 0000
13 55 0005
13 55 0011
00010
WATER
TEMP
CENT
18.5
18.4
26.4
26.4
26.3
28.9
28.8
28.3
22.2
21.7
21.6
00665
PHOS-TOT

MG/L P
0.033
0.028
0.053
0.052
0.053

0.052
0.051
0.055
00300
DO

MG/L

8.

7.
7.
8.
8.
7.
6.
6.
6.
32217




7

2
2
6
2
0
8
6
6

CHLRPHYL
A
UG/L
4.

19.


30.
11.




3

3


5
8


00077
THftNSP
SECCHI
INCHES
60

35


66


47


00031
INCDT LT
REMNING
PERCENT









0009<-
CNDUCTv •
FIELD
MICPOMK
If.
140
211
211
210
21-
21-
21-
133
132
131













4
00400
PH

su
7
6
7
7
7
3
8
6
7
6
6















.00
.90
.10
.45
.50
.60
.45
.15
.41
.67
.89













Lta 21112C2
0010 FEET .•£-"
00-10 OOMO 0062 =
T AL« NH3-N TOT Kj£w
CAC03 TOTAL
MG/L MG/L
14 u.020
15 U.020
29 0.040
30 0.030
31 0.040



40 0.050
40 0.070
41 0.070













N
MG/L
0.700
0.600
1.000
o.aoo
0.700



0.600
0.400
0.300













00630
N02&N03
N-TOTAL
MG/L
0.030
0.020
U.020
0.020
0.020



0.020
0.020
0.020













                                                                                                                  C 0 *, 1 1
                                                                                                                   0.010
                                                                                                                   o.oov
                                                                                                                   0 . '/ '* "'
                                                                                                                   0 . '. i <•

                                                                                                                   0 . ', : ^

-------
  APPENDIX E
TRIBUTARY DATA

-------
STORE! KETRIEVAL DATE  76/03/10
                                                                  32 02 25.0  095  26  10.0  4
                                                                  NEOES RIVEW
                                                                  4837S    Ib  bULLARD
                                                                  •0-XPALt.STlNE RESERVOIR
                                                                  H*Y  175  BRDli  1  MI  N«  OF
                                                                  IIE^ALES              2111204
                                                                   0000 FEET  Dtf-'TH   CLASS 00
DATE
FROM
TO
74/09/07
74/10/ 14
74/11/22
74/12/30
75/01/25
75/02/2?
75/03/23
75/04/06
75/04/18
75/05/03
75/Ci/lb
75/06/06
75/07/18
75/08/17
00630 00625
TIME DEPTH N02&N03 TOT KJEL
OF N-TOTAL N
DAY FEET
10
12
16
14
11
13
11
10
13
09
14
10
10
09
36
10
45
48
48
35
10
39
50
50
15
15
40
43
MG/L
(I
0
u
0
0
0
0
0
0
0
0
0
0
0
.120
.280
.176
,04n
.024
.024
.010
.017
.025
.010
.025
.065
.125
.035
MG/L
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
600
300
300
900
600
400
450
350
300
800
600
850
450
550
00610 00671 00665
NH3-N PHOS-OIS PHOS-TOT
TOTAL ORTHO
MG/L
0.
0.
0.
c.
0.
0.
0.
0.
0.
0.
0.
0*
0.
0.
035
040
025
024
016
016
015
020
035
030
055
085
060
055
MG/L
0.
0.
3.
0.
0.
0.
0.
0.
0*
0.
0.
0.
0.
P
005K
005K
010
010
OOBK
008K
005K
005K
005K
005K
005
005K
005
0*005K
MG/L P
0.030
0.015
0.010
0.020
0.010
0.030
0.020
0.020
0.010K
0.060
0.010
0.020
0.040
0.040
  K VALUE KNOWN TO  BE
  LESS THAN  INDICATED

-------
RETRIEVAL DATE 76/03/10
                                                           32 21  52.0 095 27 15.0 4
                                                           NEC-itS RIVE*
                                                           48      7.S CHANOLEK
                                                           T/PflLESTINE HESEKVOIk
                                                           Hrff 273 3«D6 1 Ml * JCT M HWY
                                                           IIE^ALES             211120'*
                                                            0000  FEET  OEPTh  CLASS 00
DAiE
F^OM
Tu
74/0*/07
74/10/14
74/11/23
74/12/30
75/01/26
75/U2/23
75/03/23
75/04/06
75/04/18
75/05/04
75/05/16
75/06/06
75/07/19
75/0
-------
STORE! RETRIEVAL DATE 76/03/iO
  DATE   TIME DEPTH N02J.N03
  FROM    OF
   TO    DAY  FEET
74/09/0 1
74/10/1'*
74/11/23
74/12/30
75/01/26
75/02/23
75/03/23
75/04/06
75/04/18
75/05/04
75/05/16
75/06/06
75/07/19
75/08/17
11 21
12 45
10 ?0
15 3?
10 10
10 25
11 00
11 17
14 22
09 ?.(,
13 ?0
11 00
11 25
10 16
                                                                   482*01
                                                                  32  13  00.0  095  39  40.0  4
                                                                  FLAT CREEK
                                                                  48       ID  FRANKSTON
                                                                      i5T^4E RESERvOIk
                                                                        RD 6C7 3RDG  1 MI
                                                                  11EPALES
                                                                   0000  FEET   DEPTH
                                                                                S  OF  LEAGUEVILLE
                                                                              2111204
                                                                            CLASS  00
0630
'(.N03
OTAL
iG/L
O.ObO
0.056
0.072
0.072
0.047
0.080
0.020
0.060
0.105
1.000
0.060
0.080
0.080
0.080
00625
TOT KJEL
N
MG/L
0.600
0.600
0.500
0.600
0.500
0.500
0.600
0.450
0.600
0.700
0.650
0.550
0.550
0.800
00610
NH3-N
TOTAL
Mf,/L
0.040
0.070
0.065
0.072
0.032
0.056
0.020
0.055
0.060
0.315
0.105
0.050
0.050
0.100
00671
PrlOS-DIS
ORTHO
MG/L P
0.025
0.075
0.025
0.024
0.022
0.024
0.020
0.020
0.025
0.053
0.035
0.035
0.035
0.040
00665
PHOS-TOT

MG/L P
0.040
0.102
0.040
0.040
0.060
0.040
0.045
0.050
0.060
0.060
0.080
0.070
0.070
0.130

-------
STOHET RETRIEVAL DATE 7o/03/10
  DATE   TIME DEPTH N02J.N03
  FROM    OF
   TO    DAY  FEET
7W09/07
74/10/14
74/11/23
74/12/30
75/01/36
75/02/33
75/03/23
75/04/06
75/04/18
75/05/04
75/05/16
75/06/06
75/07/19
75/08/17
11
13
10
15
10
10
11
11
14
09
15
11
11
10
45
00
45
55
25
37
20
35
40
45
16
15
40
37
                                                                 32  le 30.0 095  36  25.0  4
                                                                 KIC"oPOO CREEK
                                                                 43      15 6ROWNSBORO
                                                                 T/PALESTINE RESERVOIR
                                                                 2NOWT RD 314 8RDG  1  Ml  NE  OF  bROWNSBORO
                                                                 11EPALE.S             2111204
                                                                  0000 FEET  DEPTH  CLASS 00
0630
'{.N03
OTAL
IG/L
0.136
0.064
0.016
0.012
C.025
0.032
0.010
0.060
0.030
0.085
0.220
0.690
0.195
0.050
00625
TOT KJEL
N
MG/L
0.700
0.700
0.300
0.800
0.300
0.400
0.650
0.500
0.850
0.900
1.050
0.600
0.550
0.800
00610
NH3-N
TOTAL
MG/L
0.075
0.040
0.065
0.104
0.024
0.024
0.035
0.055
0.080
0.065
0.180
0.330
0.045
0.130
00671
PHOS-OIS
OPTMO
MG/L P
0.050
0.055
0.020
0.015
0.008
0.016
0.020
0.020
0.025
0.030
0.067
0.065
0.080
0.135
00665
PHOS-TOT

MG/L P
0.0 bO
0.097
0.020
0.030

0.040
0.050
0.060
0.060
0.060
0.140
0.120
0.110
0.250

-------
STORET RETRIEVAL DATE  76/03/10
  DATE   TIME DEPTH N02t>N03
  FROM    OF
   TO    DAY  FEET
74/09/07
74/10/1*
74/11/82
74/13/30
75/01/25
75/02/22
75/03/22
75/04/06
75/04/18
75/05/03
75/05/16
75/06/06
75/07/19
75/OB/17
09 00
11 15
15 50
14 00
10 45
12 30
10 13
12 18
13 00
09 00
14 55
09 20
09 45
09 55
                                                                 32 la 38.0 095 26 20. C 4
                                                                 48      7.5 CHftNDLEU
                                                                 T/PALESTINE RESERVOIR
                                                                 2NOAr»Y »0 2661 6HDG 2.5 HI E OF CrtANDLES
                                                                 11EFALES             2111204
                                                                  0000 FEET  DEPTH  CLASS 00
0630
K.N03
OTAL
IG/L
•J.048
0.032
C.096
0.112
0.160
0.136
0.045
0.055
0.080
0.110
0.105
0.060
0.050
0.055
00625
TOT KJEL
N
MG/L
0.400
0.300
0.200
0.800
0.300
0.500
0.300
0.200
0.350
0.650
1.150
0.350
0.275
0.300
00610
NH3-N
TOTAL
MG/L
0.025
0.025
0.025
0.048
0.008
0.032
0.025
0.035
0.045
0.055
0.095
0.050
0.027
0.025
00671
PHOS-DIS
ORTHO
MG/L P
0.020
0.020
0.005
0.016
0.008
0.016
0.010
0.010
0.010
0.020
0.025
0.050
0.027
0.025
00665
PHOS-TOT

MG/L P
0.045
0.035
0.010K
0.100
0.020
0.060
0.030
0.020
0.030
0.040
0.120
0.080
0.060
0.060
 K VALUE KNOWN TO BE
 LESS THAN INDICATED

-------
STORET RETRIEVAL DATE 7S/03/1C
7^/11/20
7^/12/30
75/01/25
75/02/22
75/03/22
75/0*»/06
75/0<»/18
75/05/03
75/05/16
75/06/06
75/07/19
75/08/17
                                                                  32 lt> 38.0 095 26 05.0 4
                                                                  BUTLC-* CKEEr.
                                                                  48      7.b CHANDLER
                                                                  T/PALESUNE RtSERVOIfc
                                                                  2NDKT KD 2661 riRUG 3.5 MI S JCT rl*Y
                                                                  IIE^ALES             2111204
                                                                   0000 FEET  DEPTH  CLASS 00
                                                                                                    31
DATE
FROM    OK
 TO    DAY
         TIME DEPTH
              FEET
       11 24
       16 00
       14 05
       10 53
       12 37
       10 22
       12 27
       13 09
       09 10
       13 ?6
       09 00
       09 55
       10 00
00630
N02&N03
N-TOTAL
MG/L
0.200
0.176
0.112
0.136
0.096
0.104
0.090
0.135
0.140
0.150
0.125
0.210
0.200
0.320
00625
TOT KJEL
N
MG/L
0.500
0.300
0.600
0.900
0.300
0.400
0.450
0.500
0.550
0.650
0.800
0.750
0.350
0.250
00610
NH3-N
TOTAL
MG/L
0.090
0.055
0.060
0.072
0.040
0.032
0.035
0.080
0.120
0.145
0.100
0.150
0.060
0.030
00671
PriOS-OIS
OPTHO
MG/L P
0.025
0.010
0.010
0.015
0.016
0.016
0.010
0.010
0.010
0.020
0.025
0.020
0.010
0.015
00665
PHOS-TOT

MG/L P
0.033
0.020
0.020
0.030
0.020
0.040
0.030
0.030
0.040
0.060
0.090
0.030
0.020
0.040

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STOSET RETRIEVAL DATE 76/03/10
                                                                  4B24F1
                                                                 32  12 45.0 095 23 45.0 4
                                                                 SALINE C^EEK
                                                                 48      SMITH CO H*Y MAP
                                                                 T/PflLESTlNE RESERVOIR
                                                                 2NDA*Y RU 2868 B«OG  10.0 MI  Srt  Of  TYLtw
                                                                 11EHALES             2111204
                                                                  0000 FEET  DEPTH  CLASS 00
  DATE    TIME  DEPTH  N02&N03
  FROM     OF
    TO     DAY   FEET
74/09/07
74/10/14
74/11/22
74/12/30
75/01/25
75/02/22
75/03/22
75/04/06
75/04/18
75/05/03
75/05/16
75/06/06
75/07/19
75/08/17
          09 52
          11 40
          16 15
          14 17
          11 11
          12 52
          10 45
          10 11
          13 25
          09 25
          13 40
          09 58
          10 10
          10 10
0630
&N03
OTAL
G/L
0.390
0.320
0.288
0.184
•J.336
0.368
0.350
0.440
0.410
0.300
0.195
0.410
0.550
0.065
00625
TOT KJEL
N
MG/L
0.600
0.300
0.400
2.300
0.400
0.500
0.450
0.200
0.600
0.750
0.850
0.550
0.500
0.550
00610
NH3-N
TOTAL
MG/L
0.040
0.040
0.055
0.176
0.080
0.088
0.045
0.080
0.125
0.125
0.105
0.095
.0.070
0.060
00671
PHOS-OIS
ORTHO
MG/L P
0.030
0.010
0.005
0.010
0.008K
0.016
0.010
0.005
0.015
0.030
0.045
0.015
0.030
0.025
00665
PHOS-TOT

MG/L P
0.090
0.037
0.010

0.030
0.050
0.030
0.020
0.050
0.060
0.100
0.030
0.070
0.070
   K ".VALOFTR'NOHN TO HE
   LESS T.HAN INDICATED

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