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
-------
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
-------
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.
-------
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
-------
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
-------
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
-------
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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