U.S. ENVIRONMENTAL PROTECTION AGENCY
               NATIONAL EUTROPHICATION SURVEY
                        WORKING PAPER SERIES
          PACIFIC NORTHWEST ENVIRONMENTAL RESEARCH LABORATORY
                        An Associate Laboratory of the
             NATIONAL ENVIRONMENTAL RESEARCH CENTER - CORVALLIS, OREGON
                                 and
       NATIONAL ENVIRONMENTAL RESEARCH CENTER - LAS VEGAS, NEVADA
•&GPO	697.032

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                                     REPORT
                                       ON
                                TYGART RESERVOIR
                          BARBOUR AND TAYLOR COUNTIES
                                 WEST VIRGINIA
                                 EPA REGION III
                             WORKING PAPER No, 470
         WITH THE COOPERATION OF THE
WEST VIRGINIA DEPARTMENT OF NATURAL RESOURCES
                  AND THE
         WEST VIRGINIA NATIONAL GUARD
                  JUNE, 1975
                                                     838

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                                   CONTENTS
                                                               Page
  Foreword                                                      i i
  List of West Virginia Study Lakes                             iv
  Lake and Drainage Area Map                                 v,  vi

  Sections
  I.   Conclusions                                                 1
 II.   Lake and Drainage Basin Characteristics                     4
III.   Lake Water Quality Summary                                 5
 IV.   Nutrient Loadings                                          9
  V.   Literature Reviewed                                       15
 VI.   Appendices                                                16

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

OBJECTIVES

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

ANALYTIC APPROACH

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

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

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

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

LAKE ANALYSIS

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

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

ACKNOWLEDGMENT

    The staff of the National Eutrophication Survey (Office of
Research & Development, U. S. Environmental Protection Agency)
expresses sincere appreciation to the West Virginia Department
of Natural Resources for professional involvement and to the
West Virginia National Guard for conducting the tributary
sampling phase of the Survey.

    Ira S. Latimer, Jr., Director of the Department of Natural
Resources; and John H. Hall, Chief of the Water Resources
Division; and the Water Resources Division staff provided
invaluable lake documentation and counsel during the Survey,
reviewed the preliminary reports, and provided critiques most
useful in the preparation of this Working Paper series.

    Major General Jack W. Blair, the Adjutant General  of West
Virginia, and Project Officer Major Manuel G. Goble, who directed
the volunteer efforts of the West Virginia National Guardsmen,
are also gratefully acknowledged for their assistance to the
Survey.

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                                    IV
LAKE NAME
Bluestone
Lynn
Summersville
Tygart
                      NATIONAL EUTROPHICATION SURVEY
                               STUDY LAKES
                          STATE OF WEST VIRGINIA
COUNTY
Mercer, Monroe, Summers,
 WV; Giles, VA
Monongalia
Nicholas
Barbour, Taylor

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GRAFTON
                   FYGART RESERVOIR
 West
Grafton
                     Tributary Sampling Site
                   X Lake Sampling Site
                       ,     ?         IKm
South
 rafton

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 TYGART RESERVOIR

9  Tributary Sampling Site
X  Lake Sampling Site
f  Sewage Treatment Facility
•b  Drainage Area Boundary
              MM.
         Scale
                                                                     _T

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                             TY6ART RESERVOIR
                             STORE! NO. 5404

I.  CONCLUSIONS
    A.  Trophic Condition:
            Survey data indicate that Tygart Reservoir is mesotrophic.
        It ranked first in overall trophic condition when the four
        West Virginia lakes sampled in 1973 were compared using a combi-
        nation of six parameters*.  None of the other lakes had less
        but one had the same median total phosphorus, one had less median
        dissolved phosphorus, none had less median inorganic nitrogen
        or mean chlorophyll a^, and one had greater mean Secchi disc
        transparency.  Marked depression of dissolved oxygen with depth
        occurred at all three sampling stations in July and at station
        1 in October.
            Much of the Tygart Valley River drainage downstream from
        the confluence of Roaring Creek (about ten kilometers west of
        El kins; see map, page vi) is impacted by acid mine wastes
        (Hall, 1975).  The effect of these wastes on the trophic condi-
        tion of Tygart Reservoir was not determined although evidenced
        by the rather low pH of the reservoir water.  It is reported
        that a continuing supply of acid substances to certain lakes
        in Sweden causes oligotrophication of those waters (Grahn et al.,
        1974); conversely, some mid-Missouri strip mine lakes are reported
        to have become early eutrophic as the acid production of the
        stripped areas gradually diminished (King et al., 1974).  The
* See Appendix A.

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                                 2
    question of controllability of acid mine wastes was not addressed
    during the Survey.
B.  Rate-Limiting Nutrient:
        The algal assay results and the high ratios of inorganic
    nitrogen to orthophosphorus measured in the reservoir indicate
    phosphorus was the limiting nutrient at all sampling times.
C.  Nutrient Controllability:
        1.  Point sources—During the sampling year, the estimated
    phosphorus contribution of point sources amounted to 11.1% of
    the total load.  The Philippi sewage treatment plant accounted
    for an estimated 7.5% of the total, and the Belington plant
    contributed an estimated 3.5%.
        The reservoir received a total phosphorus loading of 6.79
    g/m2/yr during the sampling year.  This loading is twice that
    proposed by Vollenweider (Vollenweider and Dillon, 1974) as
    a eutrophic loading (see page 14).
        Now, Vollenweider's model probably does not apply to water
    bodies with short hydraulic retention times, and the mean
    hydraulic retention time of the reservoir is a relatively short
    20 days.  However, regardless of the applicability of the model,
    Tygart Reservoir is phosphorus limited, and all phosphorus inputs
    should be reduced to the greatest practicable degree to protect
    the existing water quality.
        2.  Non-point sources—Non-point sources contributed about
    89% of the total phosphorus load during the year of sampling.
    The Tygart Valley River contributed 55.3% of the load, and 11.5%

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                             3
of the load was contributed by the remaining seven sampled
tributaries.  Unsampled tributaries and immediate drainage
accounted for an estimated 21.8% of the load.
    The phosphorus export rate of Scab Run was over six times
the mean of the export rates of the other Tygart Reservoir
tributaries (see page 13).  The high export rate resulted from
exceptionally high phosphorus concentrations in the stream in
July, August, and September of 1973 (see Appendix E).   The
cause of these high phosphorus levels is not known but may
have been due to recreational use of the area.

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II,
LAKE AND DRAINAGE BASIN CHARACTERISTICS1"
                    tt
A.  Lake Morphometry  :

    1.  Surface area:  7.08 kilometers2.

    2.  Mean depth:  17.4 meters.

    3.  Maximum depth:  53.9 meters.

    4.  Volume:  123.192 x 106  m3.

    5.  Mean hydraulic retention time:   20  days  (based on outlet flow),

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

    1.  Tributaries -
             Name

             Tygart Valley River
             Scab Run
             Frog Run
             Swamp Run
             Sandy Creek
             Teter Creek
             Laurel  Creek
             Pleasant Creek
             Minor tributaries  &
              immediate drainage -
Drainage
area (km2)*
2,447.5
4.3
3.4
9.7
207.2
138.6
140.1
32.6
547.4
Mean flow
(mVsec)*
50.1
0.1
0.1
0.2
4.5
3.1
3.1
0.7
11.3
                         Totals

         2.   Outlet -

             Tygart Valley River

     C.   Precipitation***:

         1.   Year of sampling:   135.3  centimeters.

         2.   Mean annual:   105.4 centimeters.
                                           3,530.8
                                           3,537.9**
73.2
72.7
 t  Table of metric conversions—Appendix  B.
 tt Robinson,  1974.
 *  For limits  of accuracy,  see Working  Paper No. 175, "...Survey Methods,
   1973-1976".
 ** Includes area of lake.
 *** See Working Paper No.  175.

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                                       5
III.   LAKE WATER QUALITY SUMMARY
      Tygart Reservoir was  sampled three times  during  the  open-water
  season of 1973 by means of a  pontoon-equipped Huey helicopter.   Each
  time, samples for physical  and chemical  parameters were  collected
  from three stations on the reservoir and from a  number of depths at each
  station (see map, page v).   During each  visit, a single  depth-integrated
  (4.6 m to surface) sample was composited from the stations for  phyto-
  plankton identification and enumeration; and  during  the  April 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 38.1  meters  at station 1, 28.0 meters at station 2, and
  22.9 meters at station 3.
      The sampling  results  are  presented in full in Appendix D and are
  summarized in the following table.

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PARAMETER

TEMP id

DISS OXY 

CNOCTVY (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 ( 4/23/73)

                                   3 SITES
CHEMICAL CHARACTERISTICS FOR TYGART RESERVOIR
 STORET COOE 5404

           2ND SAMPLING ( 7/28/73)

                 3 SITES
3RD SAMPLING (10/ 5/73)

      3 SITES
RANGE
8.3
9.3
70.
5.8
10.
0.004
0.002
0.440
0.020
0.200
0.470
0.640
0.5
0.9
- 17.0
- 11.1
80.
6.7
10.
- 0.013
- 0.008
- 0.500
- 0.070
- 0.600
- 0.540
- 1.080
0.9
3.7
MEAN
12.8
10.6
74.
6.5
10.
0.007
0.005
0.474
0.037
0.270
0.511
0.743
0.6
2.2
MEDIAN
11.9
10.7
75.
6.6
10.
0.006
0.005
0.480
0.030
0.200
0.510
0.690
0.5
2.1
RANGE
13.7
0.3
66.
5.8
10.
0.004
0.002
0.090
0.030
0.200
0.290
0.440
1.0
2.9
- 27.7
8.1
- 138.
6.8
18.
- 0.023
- 0.012
- 0.480
- 0.620
- 0.900
- 0.720
- 0.990
2.0
3.5
MEAN
23.2
6.0
95.
6.3
12.
0.006
0.003
0.295
0.099
0.276
0.394
0.571
1.5
3.2
MEDIAN
24.9
7.4
97.
6.1
10.
0.005
0.003
0.280
0.040
0.200
0.320
0.540
1.6
3.1
RANGE
16.7
0.4
86.
6.2
10.
0.004
0.003
0.040
0.060
0.200
0.330
0.470
1.2
3.7
- 23.7
8.6
- 132.
7.0
18.
- 0.045
- 0.009
- 0.360
- 0.590
- 0.900
- 0.630
- 0.940
1.6
4.0
MEAN
22.2
7.0
120.
6.5
12.
0.013
0.006
0.287
0.111
0.289
0.398
0.577
1.4
3.8
MEDIAN
23.2
7.4
127.
6.4
11.
0.007
0.006
0.280
o.oao
0.200
0.370
0.550
1.3
3.8

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    B.  Biological characteristics:

        1.  Phytoplankton -

            Sampling
            Date

            04/23/73
            07/28/73
            10/05/73
        2.  Chlorophyll  a_ -

            Sampling
            Date

            04/23/73
            07/28/73
            10/05/73
Dominant
Genera
1.
2.
3.
4.
5.
1.
2.
3.
4.
1.
2.
3.
4.
5.
Flagellates
Dinobryon sp.
Pennate diatoms
Nitzschia sp.
Navicula (?) sp.
Other genera
Total
Glenodinium sp.
Centric diatoms
Ankistrodesmus sp
Flagellates
Total
Microcystis SJD.
Scenedesmus SJD.
Phormidium SJK
Flagellates
Nitzschia SJD.
Other genera
                        Algal  Units
                        per ml _

                            104
                             57
                             17
                             13
                             10
                            212

                             69
                             69
                             35
                             35
                                                 Total
Station
Number

  01
  02
  03

  01
  02
  03

  01
  02
  03
                            208

                            287
                            202
                            169
                            118
                             67
                            135

                            978
Chlorophyll  a_
(ug/1 )

    0.9
    0.5*
    2.0
    1.0
    1.6

    1.3
    1.6
    1.2
* Value known to be less  than  indicated.

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0.005
0.055
0.055
0.005
0.420
0.420
1.420
1.420
0.1
11.0
14.8
0.1
                                 8
C.  Limiting Nutrient Study:
    1.  Autoclaved, filtered, and nutrient spiked -
                           Ortho P        Inorganic N    Maximum yield
        Spike (mg/1)       Cone, (mg/1)   Cone,  (mg/1)    (mg/1-dry wt.)
        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 Tygart Reservoir was low at the time  the sample was  col-
        lected (04/23/73).   The yield increased  significantly when
        orthophosphorus alone was added, but the  addition of nitro-
        gen alone had no effect on yield.   Phosphorus is  thus indicated
        as the limiting nutrient.
            Phosphorus limitation is also  indicated by  the high mean
        ratios of inorganic nitrogen to orthophosphorus measured in
        the reservoir (55 to 1 or greater  at all  sampling stations and
        times).

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IV.   NUTRIENT LOADINGS
     (See Appendix E for data)
     For the  determination  of nutrient  loadings,  the West  Virginia
 National Guard collected monthly near-surface  grab samples  from each
 of  the tributary sites  indicated on  the map  (page vi), except for the
 high runoff  months of February and March  when  two samples were collected,
 Sampling was begun in July,  1973,  and  was completed in June, 1974.
     Through  an interagency agreement,  stream flow estimates for the
 year of sampling and a  "normalized"  or average year were  provided by
 the West Virginia District Office of the  U.S.  Geological  Survey for the
 tributary sites nearest the  lake.
     In this  report, nutrient loads for sampled tributaries  were deter-
 mined by using a modification  of a U.S. Geological Survey computer
 program for  calculating stream loadings*.  Nutrient loads shown are
 those measured minus point-source  loads,  if  any.
     Nutrient loads for  unsampled "minor tributaries and immediate
 drainage "("II" of U.S.G.S.) were  estimated  using the means of the
 nutrient loads, in kg/km2/year,  at stations  C-l, D-l, E-l,  F-l, G-l,
 and H-l  and  multiplying the  means  by the  II  area in km2.
     The operator of the El kins wastewater treatment plant provided
 monthly effluent samples and corresponding flow data.  However, the
 operator of  the Philippi plant submitted  only  two samples,  and the
 operator of  the Belington  plant  did  not provide  sufficient  flow data
 *  See  Working  Paper  No.  175.

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                                    10
to permit calculation of the effluent loads.  Consequently,  the
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.
    Also, the Elkins plant is not included as a point source in this
report since it is located so far upstream from the reservoir (the
sampling data are included in Appendix E for the record, however).
    A.  Waste Sources:
        1.  Known municipal* -
Name
Philippi
Belington
Pop.
Served
3,200
1,500
Treatment
prim.
clarifier
oxidation
ditch
Mean Flow
(m3/d)
1,211.2
567.8
Receiving
Water
Tygart Valley
River
Tygart Valley
River
        2.  Known industrial - None
* Leon, 1973.

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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) -

                Tygart Valley River           26,615          55.3
                Scab Run                         495           1.0
                Frog Run                         140           0.3
                Swamp Run                        295           0.6
                Sandy Creek                    1,455   .        3.0
                Teter Creek                    1,435           3.0
                Laurel Creek                   1,080           2.3
                Pleasant Creek                   620           1.3

            b.  Minor tributaries & immediate
                 drainage (non-point load) -  10,490          21.8

            c.  Known municipal  STP's -

                Philippi                       3,630           7.5
                Belington                      1,700       .    3.5

            d.  Septic tanks* -                   15          <0.1

            e.  Known industrial - None

            f.  Direct precipitation** -         125           0.3

                        Total                  48,095         100.0

        2.  Outputs -

            Lake outlet - Tygart Valley R.    43,935

        3.  Net annual P accumulation - 4.160 kg.
* Estimate based on 61 lakeshore dwellings:  see Working Paper No.  175,
** See Working Paper No. 175.

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                                    12

    C.  Annual Total Nitrogen Loading - Average Year:

        1.  Inputs -

                                              kg N/          % of
            Source                            y_r	          total

            a. Tributaries (non-point load) -

                Tygart Valley River           897,575         63.3
                Scab Run                        3,625          0.3
                Frog Run                        2,615          0.2
                Swamp Run                       6,385          0.5
                Sandy Creek                    73,255          5.2
                Teter Creek                    55,935          3.9
                Laurel Creek                   52,085          3.7
                Pleasant Creek                 18,075          1.3

            b.  Minor tributaries & immediate-
                 drainage (non-point load) -  283,825         20.0

            c.  Known municipal STP's -

                Philippi                       10,885          0.8
                Belington                       5,100          0.4

            d.  Septic tanks* -                   650         <0.1

            e.  Known industrial - None

            f.  Direct precipitation** -        7.645          0.5

                        Total               1,417,655        100.0
                                        I

        2.  Outputs -

            Lake outlet - Tygart Valley R.  1,507,515

        3.  Net annual N loss - 89,860 kg.
* Estimate based on 61 lakeshore dwellings; see Working Paper No.  175,
** See Working Paper No. 175.

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                                13

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

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

    Tygart Valley River                        11             367
    Scab Run                                  115             843
    Frog Run                                   41             769
    Swamp Run                                  30             658
    Sandy Creek                                  7             354
    Teter Creek                                 10             404
    Laurel  Creek                                8             372
    Pleasant Creek                             19             554

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                                    14
     E.  Yearly  Loadings:
             In  the  following table, the existing phosphorus loadings
        are  compared  to  those proposed by Vollenweider (Vollenweider
        and  Dillon, 1974).  Essentially, his "dangerous" loading is
        one  at  which  the receiving water would become eutrophic or remain
        eutrophic;  his "permissible" loading is that which would result
        in the  receiving water remaining oligotrophic or becoming oligo-
        trophic if morphometry permitted.  A mesotrophic loading would
        be considered one between "dangerous" and "permissible".
             Note that Vollenweider's model may not be applicable to
        water bodies with short hydraulic retention times.
                                     Total Phosphorus        Total Nitrogen

grams/m2/yr
Total
6.79
Accumulated
0.59
Total Accumulated
200.2 loss*
        Vollenweider phosphorus loadings
         (g/m2/yr) based on mean depth and mean
         hydraulic retention time of Tygart Reservoir:
            "Dangerous"  (eutrophic loading)        3.36
            "Permissible"  (oligotrophic loading)   1.68
* There was an apparent loss of nitrogen during the sampling year.  This
  may have been due to nitrogen fixation in the lake, solubilization of
  previously sedimented nitrogen, recharge with nitrogen-rich ground
  water, or unknown and unsampled point sources discharging directly to
  the lake.  Whatever the cause, a similar loss of nitrogen has occurred
  at Shagawa Lake, Minnesota, which has been intensively studied by EPA's
  Eutrophication and Lake Restoration Branch (Malueg et al., 1975).

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                                    15

V.  LITERATURE REVIEWED

    Grahn, 0., H. Hultberg, and L.  Landner;  1974.   Oligotrophication--
        a self-accelerating process in lakes subjected to excessive
        supply of acid substances.   AMBIO,  vol.  3,  no.  2, pp.  92-93.
        Royal  Swedish Acad. of Sci., Stockholm.

    Hall, John H., 1975.   Personal  communication (acid mine wastes in
        Tygart Reservoir  drainage). WV Dept. of  Nat.  Resources,
        Charleston.

    King, Darrell L., Joseph J. Simmler,  Charles S.  Decker, and  Curtis
        W. Ogg; 1974.  Acid strip mine lake  recovery.   Jour. Water
        Poll.  Contr.  Fed., vol. 46, no.  10,  pp.  2301-2315.

    Leon, Victor, 1973.  Treatment  plant  questionnaires (Philippi and
        Belington STP's).  WV Water Resources Insp.,  Clarksburg.

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

    Robinson,  David,  1974.  Personal communication  (lake morphometry).
        WV Dept. of Nat.  Resources, Charleston.

    Vollenwider, 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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VI.   APPENDICES
                                    APPENDIX A
                                   LAKE RANKINGS

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LAKES RANKED BY INDEX NOS.




RANK  LAKE CODE  LAKE NAME               INDEX NO






   1  5404       TYGART RESERVOIR           450




   2  5402       LAKE LYNN RESERVOIR        350




   3  5403       SUMMERSVJLLE RESERVOIR     299



   4  5401       8LUESTONE RESERVOIR        100

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LAKE DATA TO BE USED IN RANKINGS

LAKE
CODE  LAKE NAME
      9LUESTONE RESERVOIR

5402  LAKE LYNN RESERVOIR

5403  SUKMERSVILLE RESERVOIR

5404  TYGART RESERVOIR
MEDIAN
TOTAL P
0.074
0,006
0.011
0.006
MEDIAN
INORG N
1.080
0.490
0.660
0.430
500-
MEAN SEC
473.700
403.222
363.818
378.667
MEAN
CHLOtfA
14.900
4.733
6.242
1.173
15-
MIN DO
11.800
14.800
14.600
14.700
MED It
oiss ohm
0.013
0.003
0.006
0.005

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PERCENT or LAKES UITH HIGHER VALUES (NUMBER or LAKES WITH HIGHER VALUES)

LAKE
CODE  LAKE NAME

5401  bLUESTONE RESERVOIR

5402  LAKE LYNN RESERVOIR

5403  SUMXERSVILLE RESERVOIR"

5404  TYGART RESERVOIR
MEOUN •
TOTAL
0 (
03 (
33 !
83 <
P
0)
2)
1)
2)
MEDIAN
ItviORG
0 (
67 (
33 (
100 (

N
0)
2)
- 1)
3)
500-

KEAN SEC
0 (
33 {
IOC (
67 (
0)
1)
3)
2)
MEAN

CnLOKA
0 (
67 (
33 (
100 (
0)
2)
1)
3)
15-

MIN 00
100 (
0 (
67 {
33 (
3)
O
2)
1)
i/£3!
AN1
OISS ORTriO P
0 t
ICO (
33 (
67 (
0>
3)
1)
2)
I ' M !J L.
NO
ICO
2bO
2«
450

-------
    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 WEST VIRGINA
                                                                3/35/75
LAKE CODE 5404     TYGAKT RESERVOIR

     TOTAL DRAINAGE AHEA OF LAKE(SQ KM)   3537.9
          SUB-DRAINAGE
TRIBUTARY  AREA(SO KM)
JAM
        FEB
MAR
                        APR
                                                          MAY
NORMALIZED FLOWS(CMS)
  JUN     JUL     AUG
SEP
OCT
                                                                                NOV
                                                                                                                  DEC
                                                                   SUMMARY
                        TOTAL DRAINAGE AREA OF LAKE
                        SUM OF SJB-ORAINAGE AREAS
                               3537.9
                               3537.7
                                    TOTAL FLOW IN
                                    TOTAL FLOW OUT
                                  882.90
                                  875.56
     MEAN MONTHLY FLOWS AND DAILY FLOWS(CMS)

TRIBUTARY   MONTH   YEAR    MEAN FLOW  DAY         FLOW  DAY

5404A1
                                           FLOW  DAY
                                                             FLOW
5404A2
7
8
9
10
11
12
1
2
3
4
5
6
7
8
9
10
11
1
2
3
4
5
6
73
73
73
73
73
73
74
74
74
74
74
74
73
73
73
73
73
74
74
74
74
74
74
9.40
26.22
23.59
39.64
97.69
183.49
209.83
108.74
110.15
75.89
53.24
167.64
7.93
20.67
10.62
25.80
80.99
134.79
84.38
93.16
75.89
49.84
117.23
28
18
15
23
16
21
18
12
15
29
20
28
28
18
17
23
25
13
11
10
21
20
16
8.72
54.93
26.11
36.53
65.41
236.16
288.83
99.11
120.06
13.11
18.63
198.78
17.84
58.90
9.20
5.95
35.11
247.21
64.56
95.43
30.02
30.02
13.03







24
30








27
24
30



                                                                    89.76
                                                                    71.64
                                                                   101.37
                                                                    81.27
                                                                    31.43
                                                                                               MEAN
5404A1
5404A2
540461
5404C1
540401
5404E1
5404F1
5404G1
5404H1
5404ZZ
3537.9
2447.5
4.3
3.4
9.7
207.2
138.6
140.1
32.6
554.3
112.70
83.25
0.17
0.11
0.34
7.65
5.10
5.10
1.13
17.56
127.14
91.18
0.17
0.14
0.40
8.21
5.66
5.66
1.27
19.82
152.34
82.12
0.20
0.17
0.45
9.91
6.51
6.51
1.56
23.79
85.23
77.87
0.14
0.11
0.31
7.08
4.81
4.61
1.13
13.31
69.09
57.77
0.11
0.08
0.23
3.68
3.40
3.40
0.85
10.76
49.55
33.98
0.06
0.06
0.14
2.97
1.98
1.98
0.42
7.65
31.71
24.07
0.06
0.03
0.11
1.98
1.27
1.42
0.28
5.10
40.49
24.07
0.03
0.03
0.08
1.56
0.99
0.99
0.25
6.23
25.77
11.61
0.03
0.03
0.06
0.85
0.57
0.57
0.14
3.96
29.45
16.14
0.03
0.03
0.06
1.42
0.99
0.99
0.23
4.53
56.35
35.68
0.06
0.06
0.14
3.11
1.98
1.98
0.42
8.78
95.71
66.54
0.14
0.11
0.28
5.66
3.96
3.96
0.99
15.01
72.72
50.14
0.10
0.08
0.22
4.49
3.09
3.10
0.72
11.34

-------
                                   TRIBUTARY FLOW  INFORMATION FOR WEST VIRGINA
                                                                                           3/85/75
LAKE CODE 5404
                   TYGART RESERVOIR
     MEAN MONTHLY FLOWS AND DAILY FLOWS(CMS)
TRIBUTARY   MONTH   YEAR
5404B1
5404C1
540401
5404E1
              7
              B
              9
             10
             11
             12
        73
        73
        73
        73
        73
        73
 1      74
 2      74
 3      74
 4      74
 5      74
 6      74
 7      73
 a      73
 9      73
10      73
11      73
12      73
 1      74
 2      74
 3      74
 4      74
 5      74
 6      74
 7      73
 8      73
 9      73
10      73
11      73
12      73
 1      74
 2      74
 3      74
 4      74
 5      74
 6      74
 7      73
 a      73
 9      73
10      73
11      73
12      73
 1      74
 2      74
 3      74
 4      74
 5      74
 6      74
                            MEAN FLOW  DAY
                                                   FLOW  DAY
0.01
0.05
0.03
0.04
0.11
0.18
0.15
0.13
0.15
0.13
0.05
0.19
0.01
0.04
0.02
0.03
0.09
0.14
0.12
0.10
0.11
0.10
0.03
0.15
0.03
0.11
0.06
0.09
0.25
0.42
0.34
0.28
0.34
0.28
0.10
0.42
0.99
1.84
1.42
3.11
7.65
9.06
7.36
6.51
7.08
6.23
2.27
9.06
28
18
15
23
16
21
18
11
15
29
20
28
28
18
15
23
16
21
18
11
15
29
20
28
28
18
15
23
16
21
18
11
15
29
20
28
28
18
15
23
16
21
18
11
15
29
20
20
0.01
0.20
0.02
0.01
0.15
0.51
0.13
0.09
0.07
0.04
0.03
0.03
U.01
U.16
0.02
0.01
0.12
0.48
0.10
0.07
0.06
0.03
0.03
0.02
0.02
0.45
0.05
0.02
0.34
1.42
0.28
0.20
0.17
0.10
0.07
0.06
1.70
7.93
1.84
1.13
9.06
29.73
7.08
5.66
5.66
<;.27
1.70
1.42







26
30










26
30










26
30










26
30



                                                                     FLOW  DAY
                                                                     0.10
                                                                     d.07
                                                                     0.06
                                                                     0.05
                                                                     0.18
                                                                     0.15
                                                                     4.25
                                                                     3.68
                                                                                       FLOW

-------
                                   TRIBUTARY FLOW INFORMATION FOR WEST VIRGINA
                                                                              3/25/75
LAKE CODE 54Q4
       TYGART RESERVOIR
     MEAN MONTHLY FLOWS AND DAILY FLOwS(CMS)
TRIBUTARY

5404F1
5404G1
5404H1
MONTH   YEAR
7
8
9
10
11
1
2
3
4
5
6
7
8
9
10
11
1
2
3
4
5
6
7
8
9
10
11
1
2
3
4
5
6
73
73
73
73
73
74
74
74
74
74
74
73
73
73
73
73
74
74
74
74
74
74
73
73
73
73
73
74
74
74
74
74
74
MEAN FLOW  DAY
0.71
1.84
0.85
2.12
5.10
8.50
4.25
4.81
4.25
4.25
7.08
0.71
1.84
0.85
2.12
5.10
8.50
4.25
4.81
4.25
4.25
7.08
0.08
0.37
0.20
0.31
0.85
1.13
0.99
1.10
0.96
0.34
1.44
28
18
17
21
25
13
11
10
21
5
16
28
18
17
21
25
13
11
10
21
5
16
28
18
17
21
25
13
11
10
21
5
16
                                       FLOW  DAY
1.13
5.95
0.57
0.85
2.55
16.99
3.96
4.53
1.70
4.53
1.42
1.13
6.23
0.57
0.85
2.55
16.99
3.96
5.10
1.70
4.53
1.42
0.07
1.53
0.06
0.06
0.40
2.10
0.68
0.82
0.37
0.48
0.24





27
24
30








27
24
30








27
24
30



FLOW  DAY
                                                                     7.08
                                                                     2.55
                                                                     2.55
                                                                     7.08
                                                                     2.55
                                                                     2.55
                                                                     0.85
                                                                     0.57
                                                                     0.48
                                                                           FLOW

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

-------
STORET RETRIEVAL DATE 75/03/35
                                                                  540401
                                                                 39 18  40.0  080  02 00.0
                                                                 TYGART RESERVOIR
                                                                 54091    WEST  VIRGINIA
DATE
FROM
TO
73/04/23








73/07/28






73/10/05






00010
TIME DEPTH WATER
OF TEMP
DAY FEET
12
12
12
12
12
12
12
12
12
14
14
14
14
14
14
14
12
12
12
12
12
12
12
55
55
55
55
55
55
55
55
55
35
35
35
35
35
35
35
55
55
55
55
55
55
55
0000
0006
0015
0022
0035
0050
0067
0087
0107
0000
0005
0025
0045
0070
0100
0125
0000
0005
0015
0025
0050
0080
0114
CENT
16
16
15
13
11
11
10
9
8
27
27
26
23
18
16
13
23
23
23
22
21
20
16

.6
.0
.5
.1
.9
.1
.4
.7
.3
.6
.5
.4
.1
.9
.7
.7
.7
.5
.4
.8
.6
.4
.7
11EPALES

00300
00

MG/L

10.3
10.3
10.8
10.9
11.1
11.0
11.1
11.1

7.8
7.8
7.5
8.1
4.1
0.4

7.6
7.2
6.2
6.4
7.6
0.4

00077 00094
TrtANSP CNDUCTVY
SECCHI FIELD
INCHES MICROMHO
36
70
70
70
70
70
70
70
80
138 96
97
97
80
71
66
70
156 127
127
127
132
120
105
88
3
00400
PH

SU

6.60
6.70
6.70
6.70
6.70
6.70
6.70
6.70
6.80
6.70
6.60
6.20
6.10
5.90
5.80
6.60
6.40
6.30
6.20
6.20
6.40
6.20

00410
T ALK
CAC03
MG/L

10K
10K
10K
10K
10K
10K
10K
10K
17
18
18
18
18
10K
10K
11
10
10
12
13
10
18
2111202
0104
00610
NH3-N
TOTAL
MG/L

0.040
0.030
0.030
0.040
0.030
0.030
0.040
0.060
0.040
0.040
0.030
0.040
0.050
0.030
0.360
0.110
0.080
0.090
0.120
0.130
0.100
0.590
FEET DEPTH
00625
TOT KJEL
N
MG/L

0.400
0.200
0.200K
0.200K
0.200K
0.200K
0.200K
0.200K
0.200
0.400
0.200K
0.200K
0.200K
0.200K
0.400
0.500
0.300
0.200K
0.200
0.300
0.300
0.900
00630
N02&N03
N-TOTAL
MG/L

0.500
0.490
0.490
0.470
0.470
0.460
0.470
0.480
0.280
0.280
0.280
0.330
0.370
0.480
0.360
0.270
0.270
0.270
0.280
0.340
0.360
0.040
00671
PHOS-OIS
ORTHO
MG/L P

0.008
0.006
0.005
0.005
0.006
0.005
0.005
0.005
0.003
0.003
0.002K
0.003
0.003
0.002K
0.003
0.008
0.007
0.005
0.003
0.007
0.009
0.006
                   K  VALUE  KNOWN  TO  BE
                   LESS  THAN  INDICATED

-------
STORE! RETRIEVAL DATE 75/03/25
DATE
FROM
TO
73/04/23








73/07/28




'

73/10/05






00665 32217
TIME DEPTH PHOS-TOT CHLRPHfL
OF A
DAY FEET
12
12
12
12
12
12
12
12
12
14
14
14
14
14
14
14
12
12
12
12
12
12
12
55
55
55
55
55
55
55
55
55
35
35
35
35
35
35
35
55
55
55
55
55
55
55
0000
0006
0015
0022
0035
0050
0067
0087
0107
0000
0005
0025
0045
0070
0100
0125
0000
0005
0015
0025
0050
0080
0114
MG/L P

0.007 ,
0.006
0.008
0.006
0.006
0.004
0.006
0.006
0.005
0.005
J.OOS
0.005
0.005
0.006
0.007
0.008
0.007
0.005
0.005
0.013
0.022
0.023
UG/L
0.9








2.0






1.3






                                                                 39 18 
-------
STORE! RETRIEVAL DATE 75/03/25
                                                                  540402
                                                                 39 16 24.0 080 00 49.0
                                                                 TYGART RESERVOIR
                                                                 54091   WEST VIRGINIA
DATE
FROM
TO
73/04/23






73/07/28





73/10/05





00010
TIME DEPTH WATER
OF TEMP
DAY FEET
13
13
13
13
13
13
13
15
15
15
15
15
15
13
13
13
13
13
13
50
50
50
50
50
50
50
20
20
20
20
20
20
20
20
20
20
20
20
0000
0006
0015
0021
0041
0061
0081
0000
0005
0025
0045
0070
0092
0000
0005
0015
0025
0050
0088
CENT
15
15
15
13
11
10
9
27
27
26
22
18
17
23
23
23
23
21
20

.7
.5
.0
.6
.4
.1
.3
.2
.0
.4
.«
.9
.4
.4
.5
.3
.2
.9
.1
00300
DO
MG/L

10
10
10
11
11
10

7
7
7
7
2

7
7
7
7
8


.0
.2
.5
.1
.0
.6

.8
.4
.0
.8
.9

.6
.2
.4
.4
.0
11EPALES

00300
DO

MG/L

10.0
10.2
10.5
11.1
11.0
10.6

7.8
7.4
7.0
7.8
2.9

7.6
7.2
7.4
7.4
8.0

00077 00094
TRANSP CNOUCTVY
SECCHI FIELD
INCHES MICKOMHO
84 75
75
75
70
75
75
75
116 105
105
138
74
69
67
150 127
128
127
128
119
109
3
00400
PH

SO
6.60
6.60
6.60
6.60
6.60
6.60
6.60
6.70
6.70
6.10
6.20
6.10
5.90
6.60
6.50
6.40
6.40
6.50
6.70

00410
T ALK
CAC03
MG/L
10K'
10K
10K
10K
10K
10K
10K
10K
10K
10K
10K
10K

10K
10K
10K
11
11
15
2111202
0085
00610
NH3-N
TOTAL
MG/L
0.030
0.020
0.030
0.030
0.030
0.040
0.070
0.040
0.040
0.060
0.050
0.040

0.080
0.080
0.090
0.070
0.080
0.080
FEET DEPTH
00625
TOT KJEL
N
MG/L
0.400
0.600
0.300
0.300
0.200
0.200
0.300
0.200K
0.200K
0.200K
0.200K
0.200K

0.400
0.200
0.200K
0.200K
0.200K
0.300
00630
N02&N03
N-TOTAL
MG/L
0.490
0.480
0.490
0.500
0.470
0.470
0.460
0.270
0.270
0.240
0.340
0.360

0.270
0.280
0.280
0.280
0.340
0.350
00671
PHOS-DIS
OHTHO
MG/L P
0.006
0.004
0.002K
0.004
0.004
0.003
0.005
0.003
0.003
0.002K
0.002
0.002

0.004
0.004
0.004
0.005
0.007
0.006
                     K VALUE KNOWN TO 8E
                     LESS THAN INDICATED

-------
STORET RETRIEVAL DATE 75/03/25
DATE
FROM
TO
73/04/23






73/07/28




73/10/05





00665 32217
TIME DEPTH PHOS-TOT CHLRPHYL
OF A
DAY FEET
13
13
13
13
13
13
13
15
15
15
15
15
13
13
13
13
13
13
50
50
50
50
50
50
50
20
20
20
20
20
20
20
20
?0
20
20
0000
0006
0015
0021
0041
0061
0061
0000
0005
0025
0045
0070
0000
0005
0015
0025
0050
OOS8
MG/L P
0.006
0.004
0.006
C.009
0.008
0.007
0.007
0.005
0.005
0.005
0.005
0.004
0.005
0.004
0.004
0.005
0.011
0.045
UG/L
0.5K






1.0




1.6





                 K VALUE KNOWN TO BE
                 LESS THAN INDICATED
                                                                  540402
                                                                 39 16 24.0 080 00 49.0
                                                                 TYGAKT RESERVOIR
                                                                 54091   *EST VIRGINIA
                                                                 11EPALES
                                                                 3
 2111202
0085 FEET
DEPTH

-------
STORET RETRIEVAL DATE 75/03/25
                                                                  540403
                                                                 39 16 03.0 079 57 38.0
                                                                 TYGART RESERVOIR
                                                                 54091   WEST VIRGINIA
DATE
FROM
TO
73/04/23







73/07/28




73/10/05





00010
TIME DEPTH WATER
OF TEMP
DAY FEET
14
14
14
14
14
14
14
14
17
17
17
17
17
13
13
13
13
13
13
20
20
20
20
20
20
20
20
00
00
00
00
00
55
55
55
55
55
55
0000
0006
0015
0022
0030
0040
0055
0073
0000
0005
0025
0050
0075
0000
0005
0015
0030
0050
0064
CENT

17
16
12
11
11
11
11
27
27
26
23
18
23
23
23
23
20
20


.0
.9
.3
.7
.4
.3
.1
.7
.5
.8
.4
.4
.6
.4
.3
.0
.7
.4
11EPALES

00300
DO

MG/L

9.3
9.8
10.5
10.7
10.8
10.9
10.7

7.7
7.4
5.6
0.3

7.4
7.4
7.5
8.4
8.6

00077 00094
TRANSP CNDUCTVY
SECCHI FIELD
INCHES MICROMHO
144 80
75
80
75
75
75
75
75
124 130
126
128
101
83
144 127
128
127
123
102
101
3
00400
PH

SU
5.80
6.10
6.20
6.30
6.40
6.50
6.50
6.50
6.60
6.50
6.10
5.90
6.00
6.30
6.50
6.40
6.40
7.00
7.00

00410
T ALK
CAC03
MG/L
10K
10K
10K
10K
10K
10K
10K
10K
10K
10K
10K
10K
11
11
11
10
10K
13
14
2111202
0077
00610
NH3-N
TOTAL
MG/L
0.040
0.030
0.030
0.040
0.040
0.030
0.040
0.050
0.050
0.040
0.050
0.110
0.620
0.070
0.070
0.060
0.070
0.060
0.070
FEET DEPTH
00625
TOT KJEL
N
MG/L
0.200
0.200K
0.200K
0.300
0.300
0.300
0.200
0.400
0.200K
0.300
0.200K
0.300
0.900
0.300
0.200K
0.200K
0.200K
0.200
0.200
00630
N02&N03
N-TOTAL
MG/L
0.440
0.440
0.440
0.470
0.480
0.480
0.480
0.480
0.250
0.250
0.240
0.320
0.090
0.280
0.280
0.270
0.290
0.350
0.360
00671
PHOS-DIS
ORTHO
MG/L P
0.004
0.005
0.007
0.007
0.007
0.004
0.002
0.004
0.002
0.002K
0.004
0.003
0.012
0.008
0.008
0.005
0.006
0.007
0.007
               K VALUE KNOWN TO  BE
               LESS  THAN  INDICATED

-------
STORE! RETRIEVAL DATE 75/03/25
DATE
FRUM
TO
73/04/23







73/07/28




73/10/05





00665 32217
TIME DEPTH PHOS-TOT CHLRPHYL
OF A
DAY FEET
14
14
14
14
14
14
14
14
17
17
17
17
17
13
13
13
13
13
13
20
20
20
20
20
20
20
20
00
00
00
00
00
55
55
55
55
55
55
0000
0006
0015
0022
0030
0040
0055
0073
0000
0005
0025
0050
0075
0000
0005
0015
0030
0050
0064
MG/L P
0
0
0
0
0
C
0
0
0
0
0
0
0
0
0
0
o
0
0
.005
.006
.006
.006
.009
.010
.009
.013
.006
.005
.004
.005
.023
.008
.007
.005
.007
.026
.034
UG/L-
0.5K







1.6




1.2





                        K VALUE KNOWN TO BE
                        LESS THAN INDICATED
                                                                  540403
                                                                 39 16 03.0 079 57 38.0
                                                                 TYGART RESERVOIR
                                                                 54091   WEST VIRGINIA
                                                                 11EPALES
                                                                 3
 2111202
0077 FEET
DEPTH

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

-------
5TOKET RETRIEVAL DATE 75/03/25
                                                                  54G4A1
                                                                 39 19 14.0 080 01 J2.0
                                                                 TYGART VALLEY RIVER
                                                                 54067   7.5 GRAFTON
                                                                 U/TYGART RES
                                                                 USGb GAGING STATlOiM UOdNbTREAM OF DAM
                                                                 11EPALES             2111204
                                                                 4                   0000 FEET  DEPTH
DATE
FROM
TO
73/07/28
73/08/18
7J/09/15
73/10/23
73/11/16
73/12/21
74/01/16
74/02/12
74/02/24
74/03/15
74/03/30
74/0^/29
74/05/20
74/06/26
OC630 00625
TIME DEPTH N02^N03 TOT KJt'L
OF N- TOTAL N
DAY FEET
16
11
11
11
10
11
10
12
13
11
11
11
11
12
00
35
30
20
00
15
20
10
40
30
55
30
25
00
MG/L
0
0
0
0
0
0
'J
0
0
0
0
0
0
0
.420
.360
.300
.288
.370
.620
.490
.490
.410
.420
.410
.360
.260
.310
MG/L
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
G.
0.
210
110
340
250
100K
300
100
200
100K
600
700
400
100K
100K
00610 00671 00665
NH3-N PHOS-DIS PHOS-TOT
TOTAL OKTHO
MG/L
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
080
G60
132
095
063
052
036
040
030
065
080
055
050
057
MG/L
0.
0.
0.
0.
0 .
0.
0.
0.
0.
0.
0.
0.
0.
0.
p
005K
024
005K
018
005K
016
008
005
005K
005K
005K
005K
002
005
MG/L P
0.015

0.015
0.018
0.005K
0.065
0.055
0.005K
0.015
0.005K
0.005K
0.010
0.005K
0.030
                     K  VALUE KNOWN  TO  BE
                     LESS  THAN  INDICATED

-------
STORET RETRIEVAL DATE 75/03/25
                                                                  5404A2
                                                                 39 12 35.0 079 59 40.0
                                                                 TYGART VALLEY RIVER
                                                                 54      7.5 NESTORVILLE
                                                                 1/TYGAHT RES
                                                                 RO BROG AT W EDGE OF ARDEN
                                                                 llEPALEb             2111204
                                                                 4                   0000 FEET
DATE
FROM
TO
73/07/28
73/08/18
73/09/17
73/10/23
73/11/25
74/01/13
74/01/27
74/02/11
74/02/24
74/03/10
74/03/30
74/04/21
74/05/20
7
-------
STOHET RETRIEVAL DATE 75/03/25
                                                                  5404B1
                                                                 39 Ib  16.0  030  00  45.0
                                                                 SCAb KUN
                                                                 54      7.5 GKAFTON
                                                                 T/TfbART  KES
                                                                 no bkjG  2 MI s  OF  PARK  VIEW
                                                                 I1EPALES              2111204
                                                                 4                   0000  FEET
DATE
FROM
TO
73/07/28
73/08/18
73/09/15
73/10/23
73/11/16
73/12/21
74/01/1H
74/02/11
74/02/26
74/03/15
74/03/30
74/04/29
74/05/20
74/00/2H
00630
TIME DE^TH N02&N03
OF N-TOTAL
DAY FEET
Ib
11
11
11
10
11
10
12
13
11
11
11
11
11
35
10
10
05
15
00
13
00
30
?0
40
15
15
40
MG/L
0
0
0
u
0
0
0
0
u
0
0
0
0
0
.315
.043
.600
.700
.200
.500
.330
.352
.26n
.232
.152
.200
.112
.168
00625
TOT KJtL
N
MG/L
0.
20.
1.
0.
0.
C.
1.
0.
0.
0.
0.
1.
3.
1.
640
000
300
900
250
100
300
100K
100K
200
700
000
ICO
000
00610 00671 00663
NHJ-N PMOS-DIS PHOS-TOT
TOTAL OkTHO
Mfa/L
0.
2.
0 .
0.
0.
0.
0.
o.
0.
0.
0.
0.
0.
u>
071
900
230
089
026
020
100
020
010
020
025
045
150
070
MG/L
0.
0.
0.
0.
0.
0.
0.
u.
0.
0.
0.
0.
0.
0.
p
130
540
058
036
008
008
008
005
010
010
005
010
007
020
MG/L P
0.220
1.350
0.240

O.Olt,
0.025
0.015
0.010
0.030
0.015
0.03b
0.010
0.035
0.065
DEPTH
                    K VALUE KNOWN TO BE
                    LESS THAN INDICATED

-------
STORE! RETRIEVAL DATE 75/03/25
                                                                  5404C1
                                                                 39 16 55.0 079 59 00.0
                                                                 FROG RUN
                                                                 54      7.5 THORNTON
                                                                 T/TYGART WES
                                                                 Ku) aRDG 5 MI S OF BLUEVILLE
                                                                 11EPALES             2111204
                                                                 4                   0000 FtET
DEPTH
DATE
FROM
TO
73/07/2H
73/OB/18
73/09/15
73/10/23
73/11/16
73/12/21
74/Ol/ltt
74/02/11
74/u2/26
74/03/15
74/03/30
74/04/29
74/05/20
74/06/28
00630 00625
TIMF. DEPTH N02kN03 TOT KJEL
OF N- TOTAL N
DAY FEET
15
10
10
10
10
10
10
11
13
11
11
11
11
11
15
55
55
52
25
45
05
45
20
10
30
00
05
30
MG/L
1
0
u
0
0
0
u
0
0
0
0
0
0
0
.020
.450
.940
.420
.310
.672
.490
.528
.470
.390
.300
.300
.352
.240
MG/L.
0.
0.
1.
0.
0.
0.
0.
0.
0.
0.
0.
1.
0.
0.
450
320
290
500
300
200
100K
100K
900
300
700
000
300
700
00610 00671 00665
NH3-N HnOS-OIS PHOS-TOT
TOTAL ORIHO
MG/L
0.
0.
0.
0.
0.
0.
C.
0.
0.
C.
0.
0.
0.
0.
198
090
075
150
U17
020
C28
040
090
025
025
070
060
035
MG/L
0.
0.
0.
0.
0.
0.
0.
0.
0.
Or
0.
0.
0.
0 .
p
092
04b
023
030
008
012
008
010
010
005
005K
005
010
010
MG/L P
0.115
0.050
0.190
0.175
0.020
0.030
0.020
0.015
0.030
0.015
0.045
O.OOSK
0.045
0.030
                    K  VALUE KNOWN  TO  BE
                    LESS  THAN  INDICATED

-------
STORET RETRIEVAL DATE 75/03/>5
                                                                  540401                            ,
                                                                 39  17 46.0 079 57 20.0
                                                                 5«IAMP RUN
                                                                 54      7.5 THORNTON
                                                                 T/TfGART KtS
                                                                 HO  3KUG .5 MI SE OF MILLERTOWIM
                                                                 11EPALES              211120t
                                                                 4                   0000  FEET   DEPTH
DATE
FROM
TO
73/07/28
73/08/18
73/09/15
73/10/23
73/11/16
73/12/21
7^/01/16
74/02/11
74/02/26
74/03/15
7^/03/30
74/04/29
74/05/20
7W06/28
OC630 00625
TIME DEPTH N02NN03 TOT KJEL
OF ri-TOTAL N
DAY FEET
!<*
10
10
10
10
10
09
11
13
11
11
10
10
11
55
40
40
40
45
35
50
35
10
00
15
50
55
15
MG/L
0
0
1
0
0
0
0
0
0
0
0
0
0
0
.280
.231
.800
.310
.399
.650
.570
.588
.520
.480
.300
.208
.200
.330
MG/L
0.
0.
3.
0.
0.
0.
1.
0.
0.
0.
0.
0.
0.
0.
600
310
700
550
850
300
700
1COK
100
300
300
700
300
700
00610
NH3-N
TOTAL
MG/L
0
0
0
0
0
0
0
0
0
0
0
0
0
0
.110
.098
.560
.083
.063
.020
.136
.030
.030
.020
.015
.150
.050
.065
00671 00665
PHOS-OIS PHOb-TOT
ORFHO
MG/L
0.
0.
0.
0.
0.
0.
0.
- 0.
0.
o.
0.
0.
0.
0.
p
021
020
132
023
008
008
008
005
010
005K
005
010
007
005K
MG/L P
0.055
0.040
0.525
0.180
0.040
0.035
0.030
0.015
0.025
0.025
0.025
0.010
0.045
0.035
                    K VALUE KNOWN TO BE
                    LESS THAN INDICATED

-------
STORET RETRIEVAL DATE 75/03/25
                                                                  5404E1
                                                                 39 17 10.0 079 56 00.0
                                                                 SANDY CHEEK
                                                                 54      7.5 THORNTON
                                                                 T/TYGART KtS
                                                                 kL> BROG IN VILLAGE Of HIRAM
                                                                 11EPALLS             2111204
                                                                 4                   0000 FEET
DEPTH
DATE
FROM
TO
73/07/28
73/08/18
73/09/15
73/10/23
73/11/16
73/12/21
74/01/18
74/02/11
74/02/26
74/03/15
74/03/3U
74/04/29
74/05/20
7<+/ 06/28
00630 00625
TIME DEPTH N02&N03 TOT KJEL
OF N-TOTAL N
DAY FEET
14
10
10
10
10
10
09
11
13
10
09
11
10
11
40
25
?5
30
50
25
42
25
00
50
55
40
45
05
MG/L
0
0
0
0
0
0
0
t>
0
0
0
0
0
0
.280
.336
.180
.280
.336
.520
.440
.450
.410
.340
.288
.18*4
.IbO
.260
MG/L
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
340
230
IBO
250
150
300
100K
100K
200
200
300
100
lOOK
100K
00610 00671 00665
NH3-N PHOS-OIS PhOb-TOT
TOTAL ORTHO
MG/L
0.
0.
0.
0.
J.
0.
0.
0.
c.
0.
0.
0.
0.
0.
153
llu
120
07b
041
032
052
030
030
030
030
020
055
050
MG/L P
0
0
0
0
0
0
u
0
0
0
0
0
0
0
.007
.006
.009
.012
.005K
.005K
.005K
.005K
.005
.OObK
.005K
.OObK
.005K
.OOSK
MG/L P
0.007
0.006
0.020

0.010
0.035
0.005
O.OOS
O.Olb
0.005K
0.005K
0.010
C.005K
0.005K
                   K VALUE KNOWN TO BE
                   LESS THAN INDICATED

-------
STORET RETRIEVAL DATE 75/03/25
DATE
FROM
TO
73/07/28
73/J8/18
73/09/17
73/10/21
73/11/25
74/01/13
74/01/27
7^/02/11
74/02/24
74/i/J/iO
74/03/30
74/04/21
74/05/05
74/06/16
TIME 1
OF
DAY i
11 39
11 05
11 00
11 15
11 27
11 00
11 35
14 45
11 06
10 25
10 00
11 25
0V 40
10 05
              FEET
                                                                  5404F1
                                                                 39 id 40.0 079 56 00.0
                                                                 TETER CREtK
                                                                 54      7.5 NESTORVILLE
                                                                 T/TYGART RES
                                                                 bANK dtLO CONFLUENCE WITH GLAUE RUN
                                                                 11EPALES             211120^
                                                                 4                   0000 FEET  DEPTH
0630
kN03
OTAL
G/L
0.154
0.170
0.950
0.230
0.276
0.460
0.384
0.410
0.352
0.340
0.276
0.224
0.240
0.30U
00625
TOT KJEL
N
MG/L
0.170
O.lOOK
0.220
0.300
O.lOOK
O.lOOK
O.lOOK
O.lOOK
0.400
0.200
0.300
0.300
0.200
0.6CU
00610
NHJ-N
TOTAL
MG/L
0.026
0.028
u.017
0.019
0.020
0.016
0.016
0.010
0.025
0.010
0.020
0.020
0.035
0.025
00671
PnOS-UlS
ORTrlO
MG/L P
0.006
0.007
0.008
0.011
0.005K
0.006
0.005K
0.005K
0.005
0.005K
0.005K
0.005
0.003
0.005
00665
PHOb-TOT

MG/L P
0.010
0.016
0.015

0.015
0.010
0.005K
0.010
0.015
0.04J
0.015
0.010
0.015

                     K VALUE KNOWN TO BE
                     LESS THAN INDICATED

-------
STORE! RETRIEVAL DATE 75/03/25
                                                                  540<*G1
                                                                 39 11 50.0 079 56 *3.0
                                                                 LAUREL CREEK
                                                                 54      7.5 NtSTORVILLE
                                                                 T/TYGART RES
                                                                 RO dRDG 5 MI WSta Of MOATSVILLE
                                                                 HEPALtS             2111204
                                                                 4                   0000 fEET
DEPTH

DATE
FROM
TO
73/07/28
73/U8/18
73/09/17
73/10/21
73/11/25
74/01/13
7W01/27
74/02/11
74/02/24
74/03/10
74/03/30
74/04/21
74/05/0=>
7<»/06/16

TIME DEPTH
OF
DAY FEET
11 05
10 48
11 20
11 15
11 10
10 45
11 20
14 30
10 50
10 10
10 00
11 07
09 50
09 50
00630
N02&N03
N-TOTAL
MG/L
u.270
0.160
0.260
U.176
0.192
0 . 384
0.33o
0.368
0.310
0.260
0.232
0.200
J.138
U.22<*
00625
TOT KJEL
N
MG/L
0.210
0.140
0.320
0.300
0.100K
O.lOOK
0.100K
O.lOOK
O.lOOK
0.200
1.000
0.300
0.200
0.700
00610
NH3-N
TOTAL
MG/L
0.015
0.018
0.017
0.030
0.016
0.016
0.016
0.020
0.010
0.025
0.030
0.020
0.035
0.047
00671
PnOS-DIS
ORTrtO
MG/L P
0.005K
0.005K
0.006
0.009
0.005K
0.012
0.005K
0.005H
0.005
0.005K
O.OOb
0.005K
0.005K
O.OObK
00665
PHOS-TOT

MG/L P
0.005K
0.005K
0.020

0.010
0.012
0.005K
O.OObK
0.015
0.015
O.OlD
0.010
O.Olb

                  K VALUE KNOWN TO BE
                  LESS THAN INDICATED

-------
STORET RETRIEVAL DATE 75/03/25
                                                                  5404H1
                                                                 39 14 50.0 080 01 25.0
                                                                 PLEASANT CKEEK
                                                                 54      7.5 PHILLIPPI
                                                                 T/TYGART RtS
                                                                 KG rfKDG 9 MI N OK PHILLIPH1
                                                                 11EPALES             2111204
                                                                 4                   0000 FEET
DEPTH
DATE
FROM
10
73/07/28
73/08/18
73/09/17
73/10/21
73/11/25
74/01/13
74/01/27
74/02/11
74/02/24
74/03/10
74/03/30
7^/04/21
74/05/05
74/06/16
30630 00625
TIME DEPTH NO?\NOJ TuT KJEL
OF N-TOTAL N
DAY FEET
10
10
12
10
10
10
10
14
10
09
09
C9
10
09
10
05
05
40
35
10
40
00
10
40
20
45
22
15
MG/L
0
3
0
0
0
0
0
0
0
0
0
0
0
0
.032
.064
.010K
.033
.192
.710
.450
.510
.440
.360
.268
,20a
.132
.084
MG/L
0.
0.
1.
0.
0.
0.
0.
0.
0.
0.
0.
2.
0.
0.
«+40
440
000
400
100
100K
200
100
100*
500
bOO
GOO
400
750
OOblO 00671 00665
NH3-N PHOS-OIS PHOS-TOT
"lUTAL ORTHO
MG/L
0
C
0
0
0
0
0
0
0
0
0
0
0
0
.078
.093
.010
.047
.044
.016
.024
.10u
.012
.025
.040
.110
.040
.060
MG/L
0.
0.
0.
0.
0 .
0.
0.
0.
0.
0.
0.
0.
0.
0.
p
006
007
006
009
005K
008
005K
005K
007
005K
005.K
005K
005K
005K
MG/L P
0.025
0.020
0.09b

0.02t>
0.020
0.005K
0.005K
0.015
0.025
0.030
0.025
0.025
0.040
                    K VALUE KNOWN TO BE
                    LESS THAN INDICATED

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STORET RETRIEVAL DATE 75/03/25
                      00630
  DATE   TIME DEPTH N02MM03
  FROM    OF        N-TOTAL
   TO    DAY  FEET    MG/L
73/08/2d 10 00
73/09/28 10 00
0.176
0.780
                                                                  5404AA          PR5404AA
                                                                 39 09 20.0 080 02 40.0
                                                                 PHILIPPI
                                                                 54067   7.5 PHILIPPI
                                                                 T/TYGART RESERVOIR
                                                                 TYGART VALLEY RIVER
                                                                        P003200
11EPALES
4
00625
TOT KJEL
N
MG/L
0.200
0.800
00610
(MH3-N
TOTAL
MG/L
0.176
0.670
00671
PHOS-OIS
ORTHO
MG/L P
0.056
0.040
00665
PH05-TOT
MG/L P
0.085
0.395
50051
FLOW
RATE
INST MGD
0.251
0.450
2141204
0000 FEET
50053
CONDUIT
FLOW-MGD
MONTHLY
0.489
0.194
                                                                                                DEPTH

-------
STORE! RETRIEVAL DATE 75/03/25
                                                                  5404AB          TF5404AB     P006000
                                                                 39 01 30.0 079 07 00.0
                                                                 ELKINS
                                                                 54      aARbOUR COUNTY
                                                                 T/TYGART RESERVOIR
                                                                 TYGART VALLEY RIVER
                                                                 11EPALES             2141204
                                                                 4                   0000 FEET  DEPTH
DATE
FROM
TO
73/09/19
CP(D-
73/09/19
73/10/24
CH < T > -
73/10/24
73/12/03
cpm-
73/12/03
74/01/15
CP
-------
STORET RETRIEVAL DATE 75/03/25
                                                                  5404AC          005404AC     P001500
                                                                 38 55 30.0 079 52 30.0
                                                                 BELINGTON
                                                                 54      RANDOLPH COUNTY
                                                                 T/TYGART RESERVOIR
                                                                 TYGART VALLEY RIVEK
                                                                 11EPALES             2141204
                                                                 4                   0000 FEET  DEPTH
DATE
FROM
TO
73/08/17
73/09/07
73/10/19
73/11/21
73/12/19
74/01/18
74/02/22
74/03/23
74/04/22
74/09/06
74/10/29
00630
TIME DEPTH N02&N03
OF N-TOTAL
DAY FEET
11
09
09
11
11
10
09
11
11
09
10
00
00
00
00
00
00
00
00
00
30
00
MG/L
0
1
0
0
0
1
1
J
0
2
0
.450
.100
.960
.190
.660
.000
.OOU
.840
.320
.300
.640
00625
TOT KJEL
N
MG/L
5.
12.
13.
9.
7.
7.
6.
6.
7.
4.
8.
000
600
500
600
100
600
600
000
200
000
800
00610 00671 00665 50051 50053
NH3-N PHOS-DIS PHOS-TOT FLOW CONDUIT
TOTAL ORTHO RATE FLOW-MGD
MG/L
1 . 800
5.900
6.700
4.700
2.400
3.200
2.600
2.200
3.100
2.400
4.600
MG/L P
1.
3,
5,
3,
1.
2,
1.
1.
1.
1.
2,
,500
,700
,200
,363
,400
,080
,700
,000
.400
,350
,800
MG/L
2.
4.
6.
4.
2.
3.
3.
2.
3.
1.
3.
P INST MGD MONTHLY
100
500
600
100
500
800
400
400
000
600 0.335
200 0.335

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