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
697-032
-------
REPORT
ON
LAfcLYNN
MQNONGALIA COUNTY
WEST VIRGINIA
EPA REGION III
WORKING PAPER No, 468
WITH THE COOPERATION OF THE
WEST VIRGINIA DEPARTMENT OF NATURAL RESOURCES
AND THE
WEST VIRGINIA NATIONAL GUARD
JUNE, 1975
836
-------
CONTENTS
Page
Foreword i i
List of West Virginia Study Lakes iv
Lake and Drainage Area Map v> V1
Sections
I. Conclusions 1
II. Lake and Drainage Basin Characteristics 4
III. Lake Water Quality Summary 5
IV. Nutrient Loadings 9
V. Literature Reviewed 13
VI. Appendices 14
-------
ii
FOREWORD
The National Eutrophication Survey was initiated in 1972 in
response to an Administration commitment to investigate the nation-
wide threat of accelerated eutrophication to 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,b)]s
and water quality monitoring [§106 and §305(b)] activities mandated
by the Federal Water Pollution Control Act Amendments of 1972.
-------
111
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.
-------
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
-------
PENNSYLVANIA
WEST VIRGINIA"
39 "44-
Map Location
39°40' 1
LAKE LYNN
Tributary Sampling Site
Lake Sampling Site
? . IKm.
Scale
79°46'
-------
Tributary Sampling Site
* Lake Sampling Site
Sewage Treatment Facility
Drainage Area Boundary
-------
LAKE LYNN
STORE! NO. 5402
I. CONCLUSIONS
A. Trophic Condition:
Survey data indicate that Lake Lynn is mesotrophic. It
ranked second in overall trophic quality when the four West
Virginia lakes sampled in 1973 were compared using an index of
six parameters*. None of the other lakes had less but one had
the same total phosphorus, none had less median dissolved phos-
phorus, one had less inorganic nitrogen, one had less mean
chlorophyll a_, and two had greater mean Secchi disc transparency.
Near-depletion of dissolved oxygen with depth occurred at sta-
tion 3 in July and October.
The Lake Lynn drainage is impacted by acid mine wastes (Hall,
1975). The effect of these wastes on the trophic condition of
the lake was not determined although evidenced by the rather
low pH of the lake 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 question of con-
trollability of acid mine wastes was not addressed during the
Survey.
* See Appendix A.
-------
2
B. Rate-Limiting Nutrient:
The algal assay results indicate phosphorus limitation
at the time the sample was taken (04/24/73). The lake data
indicate phosphorus limitation at the other sampling times as
well.
C. Nutrient Controllability:
1. Point sources—Known point sources accounted for only
0.2% of the total phosphorus load reaching Lake Lynn during
the sampling year. These sources include the wastewater
treatment plant at Rowlesburg and septic tanks serving dwellings
near the lake.
The total phosphorus loading of 8.65 g/m2/yr is over twice
that proposed by Vollenweider (Vollenweider and Dillon, 1974)
as a eutrophic loading (see page 12). The combination of a
mesotrophic condition and relatively high phosphorus loading
is possible because Vollenweider's model probably is not
applicable to lakes with short hydraulic retention times, and
the mean hydraulic retention time of Lake Lynn is a short 12
days. In any case, it does not appear likely that point-source
phosphorus control would result in any appreciable improvement
in the trophic condition of the lake.
2. Non-point sources—It is calculated that non-point
sources contributed over 99% of the total phosphorus load to
the lake. The Cheat River contributed 93.7%; Rubles Run, 0.6%;
Coles Run, less than 0.1%; Whites Run, 1.3%; Unnamed Stream
E-l, 3.1%; and an estimated 0.9% was contributed by minor tribu-
-------
3
taries and immediate drainage.
The phosphorus export rates of White Run and Unnamed Stream
E-l were very high, particularly the rate of the latter (see
page 11). As far as is known, neither stream is impacted by a
point source, and further study is needed to determine the
cause of the high export rates.
-------
II. LAKE AND DRAINAGE BASIN CHARACTERISTICS1"
A. Lake Morphometry :
1. Surface area: 7.00 kilometers2.
2. Mean depth: 12.8 meters.
3. Maximum depth: 26.8 meters. .
4. Volume: 89.600 x 106 m3.
5. Mean hydraulic retention time: 12 days.
B. Tributary and Outlet:
(See Appendix C for flow data)
1. Tributaries -
Drainage Mean flow
Name area (km2)* (m3/sec)*
Cheat River 3,548.3 85.9
Rubles Run 32.1 0.7
Coles Run 4.2 0.1
Whites Run 7.8 0.2
Unnamed Stream E-l 4.0 0.1
Minor tributaries &
immediate drainage - 51.1 1.4
Totals 3,647.5 88.4
2. Outlet -
Cheat River 3,654.5** 88.4**
C. Precipitation***:
1. Year of sampling: 131.8 centimeters.
2. Mean annual: 102.7 centimeters.
t Table of metric equivalents—Appendix B.
tt Robinson, 1974.
* For limits of accuracy, see Working Paper No. 175, "...Survey Methods,
1973-1976".
** Includes area of lake; outlet flow adjusted to equal sum of inflows.
*** See Working Paper No. 175.
-------
III. LAKE WATER QUALITY SUMMARY
Lake Lynn 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 lake and from a number of depths at each
station (see map, page v). During each visit, a single depth-integrated
(4.6 m or near bottom to surface) sample was composited from the stations
for phytoplankton identification and enumeration; and during the first
visit, a single 18.9-liter depth-integrated sample was composited for
algal, assays. Also each time, a depth-integrated sample was collected
from each of the stations for chlorophyll a. analysis. The maximum
depths sampled were 11.0 meters at station 1, 21.3 meters at station 2,
and 23.5 meters at station 3.
The sampling results are presented in full in Appendix D. and are
summarized below.
-------
PARAMETER
TEMP (C)
DISS OXY (MG/L>
CNDCTVY (MCROMO)
PH (STAND UNITS)
TOT ALK (MG/L)
TOT P
-------
B. Biological characteristics:
1. Phytoplankton -
Sampling
Date
04/24/73
07/28/73
10/05/75
Dominant Algal Units
Genera per ml
1.
2.
3.
4.
1.
1.
2.
3.
4.
5.
Flagellates
Pinnularia sp.
Closterium sp.
Euglena sp.
Total
Glenodinium (?) sp.
Total
Kirchneriella sp.
Glenodinium (?) sp.
Flagellates
Navicula sp.
Xanthidium (?) sp.
21
10
10
10
52
657
657
441
286
66
11
11
2. Chlorophyll a^ -
Total
815
Sampling
Date
04/24/73
07/28/73
10/05/73
Station
Number
01
02
03
01
02
03
01
02
03
Chlorophyll a
(ug/1)
0.5*
0.5*
0.5*
11.9
15.9
8.1
1.4
2.2
1.6
* Value known to be less than indicated.
-------
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 0.005 0.495 0.1
0.050 P 0.055 0.495 1.3
0.050 P + 1.0 N 0.055 1.495 4.2
1.0 N 0.005 1.495 0.1
2. Discussion -
The control yield of the assay alga, Selenastrum Capri-
cornutum, indicates that the potential primary productivity
of Lake Lynn was low at the time the sample was collected.
The yield increased with the addition of orthophosphorus
alone but not with the addition of nitrogen alone. This indi-
cates phosphorus was the limiting nutrient.
Further evidence of phosphorus limitation is provided
by the mean lake inorganic nitrogen/orthophosphorus ratios
of 176/1, 163/1, and 140/1 measured in April, August, and
October, respectively.
-------
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 determined
by using a modification of a U.S. Geological Survey computer program for
calculating stream loadings*. Nutrient loads shown are those measured
minus point-source loads, if any.
Nutrient loads for unsampled "minor tributaries and immediate drainage"
("ZZ" of U.S.G.S.) were estimated using the means of the nutrient loads, in
kg/km2/year, at stations B-l and C-l and multiplying the means by the ZZ
area in km2.
The operator of the Rowlesburg wastewater treatment plant provided
monthly effluent samples and corresponding flow data.
* See Working Paper No. 175.
-------
10
A. Waste Sources:
1. Known municipal -
Name
Pop.
Served
Treatment
Mean Flow
(m'/d)
302.8
Rowlesburg* 950 lagoon
2. Known industrial - None
B. Annual Total Phosphorus Loading - Average Year:
1. Inputs -
Source
a. Tributaries (non-point load) -
Cheat River
Rubles Run
Coles Run
Whites Run
Unnamed Stream E-l
b. Minor tributaries & immediate
drainage (non-point load) -
c. Known municipal STP's -
Rowlesburg
d. Septic tanks** -
e. Known industrial - None
f. Direct precipitation*** -
Total
Outputs -
Lake outlet - Cheat River
kg P/
yr
535
85
35
125
60,575
24,250
3. Net annual P accumulation - 36,325 kg.
Receiving
Water
Cheat River
% of
total
56,755
340
40
800
1,860
93.7
0.6
<0.1
1.3
3.1
0.9
0.1
0.2
100.0
* Leon, 1973.
** Estimate based on 129 lakeshore dwellings; see Working Paper No. 175.
*** See Working Paper No. 175.
-------
11
C. Annual Total Nitrogen Loading - Average Year:
1. Inputs -
x
kg N/ % of
Source y_r total
a. Tributaries (non-point load) -
Cheat River 2,062,800 95.4
Rubles Run 29,150 1.3
Coles Run 3,860 0.2
Whites Run 7,720 0.4
Unnamed Stream E-l 2,210 0.1
b. Minor tributaries & immediate
drainage (non-point load) - 46,680 2.2
c. Known municipal STP's -
Rowlesburg 395 <0.1
d. Septic tanks* - 1,375 <0.1
e. Known industrial - None
f. Direct precipitation** - 7.555 0.3
Total 2,161,745 100.0
2. Outputs -
Lake outlet - Cheat River 2,061,655
3. Net annual N accumulation - 100,090 kg.
D. Mean Annual Non-point Nutrient Export by Subdrainage Area:
Tributary kg P/km2/yr kg N/km2/yr
Cheat River 16 581
Rubles Run 11 908
Coles Run 10 919
Whites Run 103 990
Unnamed Stream E-l 465 552
* Estimate based on 129 lakeshore dwellings; see Working Paper No. 175.
** See Working Paper No. 175.
-------
12
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
oligotrophic 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
Total Accumulated Total Accumulated
grams/m2/yr 8.65 5.19 308.8 14.3
Vollenweider phosphorus loadings
(g/m2/yr) based on mean depth and mean
hydraulic retention time of Lake Lynn:
"Dangerous" (eutrophic loading) 3.70
"Permissible" (oligotrophic loading) 1.85
-------
13
LITERATURE REVIEWED
Grahn, 0., H. Hultberg, and L. Landner; 1974. 01igotrophication--
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
Lake Lynn drainage). WV Dept. of Nat. Resources, Charleston.
King, Darrell L., Joseph J. Simmler, Charles S. Decker, and Curtis
W. Ogg; Acid strip mine lake recovery. Jour. Water Poll. Contr.
Fed., vol. 46, no. 10, pp. 2301-2315.
Leon, Victor, 1973. Treatment plant questionnaire (Rowlesburg
STP). WV Water Resources Insp., Clarksburg.
Robinson, David, 1974. Personal communication (lake morphometry).
WV Dept. of Nat. Resources, Charleston.
Vollenweider, R. A., and P. J. Dillon, 1974. The application of
phosphorus loading concept to eutrophication research. Nat!.
Res. Council of Canada Publ. No. 13690, Canada Centre for Inland
Waters, Burlington, Ontario.
-------
VI. APPENDICES
APPENDIX A
LAKE RANKINGS
-------
LAKES RANKED BY INDEX NGS.
RANK LAKE CODE LAKE NAME INDEX NO
1 5404 TYGART RESERVOIR 450
2 5402 . LAKE LYNN RESERVOIR 350
3 5403 SUMMERSVILLE RESERVOIR 299
4 5401 BLUESTONE RESERVOIR 100
-------
LAKE DATA TO BE USED IN RANKINGS
LAKE MEDIAN MEDIAN 500- MEAN 15- MEDIAN
CODE LAKE NAME TOTAL P INORG N MEAN SEC CHLORA MlN DO DISS ORTHO P
5401 BLUESTONE RESERVOIR 0.074 1.080 473.700 14.900 11.800 0.018
5402 LAKE LYNN RESERVOIR 0.006 0.490 403.222 4.733 14.800 0.003
5403 SUMMERSVILLE RESERVOIR,. 0.011 0.660 363.818 6.242 14.600 0.006
5404 TYGART RESERVOIR 0.006 0.430 378.667 1.178 14.700 0.005
-------
PERCENT OF LAKES WITH HIGHER VALUES (NUMBER OF LAKES WITH HIGHER VALUES)
CODE LAKE NAME
5401 BLUESTONE RESERVOIR
5402 LAKE LYNN RESERVOIR
5403 SUMMERSVILLE RESERVOIR''
5404 TYGART RESERVOIR
MEDIAN
TOTAL P
0 (
83 (
33 (
33 (
0)
2)
1)
2)
MEDIAN
INORG
0 (
67 (
33 (
100 (
N
0)
2)
1)
3)
500-
MEAN SEC
0 (
33 (
100 (
67 (
0)
1)
3)
2)
MEAN
CHLORA
0 (
67 (
33 (
100 (
0)
2)
1)
3)
15-
MIN DO
100 (
0 (
67 (
33 (
3)
0)
2)
1)
MED I AM
DISS ORTHO f
0 (
100 (
33 (
67 (
0>
3)
i)
2)
INOEX
NO
IOC
3bO
2$y
450
-------
APPENDIX B
CONVERSION FACTORS
-------
CONVERSION FACTORS
Hectares x 2.471 = acres
Kilometers x 0.6214 = miles
Meters x 3.281 = feet
Cubic meters x 8.107 x 10"4 = 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
3/25/75
LAKE CODE 5402
LAKE LYNN
TOTAL DRAINAGE AREA OF LAKE(SO KM) 3654.5
SUB-DRAINAGE
TRIBUTARY AREAtSQ KM)
JAN
FEB
MAR
APR
MAY
NORMALIZED FLOWS(CMS)
JUN JUL AUG
SEP
OCT
NOV
DEC
MEAN
5402A1
5402A2
5402B1
5402C1
5402D1
5402E1
5402ZZ
3654.5
3548.3
32.1
4.2
7.8
4.0
57.0
129.41
125.44
1.27
0.17
0.28
0.17
1.98
142.72
138.47
1.13
0.17
0.28
0.14
2.27
170.75
165.65
1.42
• 0.20
0.42
0.17
2.69
136.49
132.52
1.13
0.14
0.28
0.14
2.12
106.47
103.36
0.85
0.11
0.20
0.11
1.70
64.00
62.01
0.42
0.08
0.11
0.06
0.99
44.17
42.76
0.28
0.06
0.08
0.03
0.71
44.17
42.76
0.23
0.03
0.06
0.03
0.71
24.64
23.79
0.20
0.03
0.06
0.03
0.42
38.51
37.38
0.28
0.06
0.08
0.03
0.57
59.47
57.77
0.57
0.06
0.11
0.06
0.65
104.49
101.37
O.U5
0.11
0.23
0.11
1.56
88.52
85.86
0.72
0.10
0.18
0.09
1.38
TOTAL DRAINAGE AREA OF LAKE
SUM OF SUB-DRAINAGE AREAS
MEAN MONTHLY FLOWS AND UAILY FLOWS(CMS)
TRIBUTARY MONTH YEAR
5402A1
MEAN FLOW DAY
5402A2
7
8
9
10
11
12
1
2
3
4
5
6
7
8
9
10
11
12
1
2
3
4
5
6
73
73
73
73
73
73
74
74
74
74
74
74
73
73
73
73
73
73
74
74
74
74
74
74
3654.5
3653.4
FLOW DAY
20.39
39.08
21.52
60.03
129.12
193.69
220.59
119.78
147.81
131.39
95.14
205.01
19.54
37.66
20.95
58.33
125.16
187.74
214.08
116.10
143.28
127.43
92.31
198.78
29
18
15
27
18
27
12
3
14
30
20
22
29
18
15
27
18
27
12
3
14
30
20
22
22.37
77.87
25.77
11.75
124.31
1141.17
682.44
83.82
119.21
37.66
71.64
348.30
15.01
75.32
24.92
11.38
120.35
1107.19
662.61
81.27
115.53
36.53
69.38
336.97
28
30
28
30
SUMMARY
TOTAL FLO* IN
TOTAL FLO* OUT
FLOW DAY
FLOW
83.25
54.37
80.70
52.67
1062.97
1065.28
-------
TRIBUTARY FLOW INFORMATION FOR WEST VIRGINA
3/35/75
LAKE CODE 5402
LAKE LYNN
MEAN MONTHLY FLOWS AND DAILY FLOWS(CMS)
TRIBUTARY MONTH YEAR MEAN FLOW DAY
5402B1
5402C1
540201
5402E1
7
8
9
10
11
12
1
2
3
4
5
6
7
8
9
10
11
12
1
2
3
4
5
6
7
8
9
10
11
12
1
2
3
4
5
6
7
8
9
10
11
12
1
2
3
4
5
6
73
73
73
73
73
73
74
74
74
74
74
74
73
73
73
73
73
73
74
74
74
74
74
74
73
73
73
73
73
73
74
74
74
74
74
74
73
73
73
73
73
73
74
74
74
74
74
74
0.19
0.23
0.11
0.31
1.02
1.56
2.04
0.62
1.13
1.02
1.08
1.27
0.03
0.03
0.01
0.04
0.14
0.21
0.27
0.08
0.15
0.14
0.14
0.17
0.05
0.05
0.03
0.07
0.25
0.37
0.48
0.15
0.27
0.25
0.26
0.31
0.02
0.03
0.01
0.04
0.13
0.20
0.25
0.08
0.14
0.13
0.13
0.16
29
18
25
27
18
27
12
3
14
30
20
22
29
18
15
27
18
27
12
3
14
30
20
22
29
18
15
27
18
27
12
3
14
30
20
22
29
18
15
27
18
27
12
3
14
30
20
22
FLOW DAY
0.10
0.25
0.23
0.06
1.08
6.34
5.72
0.71
0.82
0.26
1.22
1.44
0.01
0.03
0.03
0.01
0.14
0.82
0.76
0.09
0.11
0.03
0.16
0.19
0.03
0.06
0.06
0.01
0.26
1.53
1.39
0.17
0.20
0.06
0.28
0.34
0.01
0.03
0.03
0.01
0.13
0.79
0.71
0.09
0.10
0.03
0.15
0.18
28
30
28
30
28
30
28
30
FLOW DAY
FLOW
0.65
0.51
0.08
0.07
0.16
0.12
0.08
0.06
-------
APPENDIX D
PHYSICAL and CHEMICAL DATA
-------
STORET RETRIEVAL DATE 75/03/25
540201
39 40 48.0 079 52 05.0
LAKE LYNN RESERVOIR
54061 WEST VIRGINIA
DATE
FROM
TO
73/04/24
73/07/28
73/10/05
TIME DEPTH
OF
DAY FEET
09 05 0000
09 05 0006
09 05 0014
13 45 0000
13 45 OOOS
13 45 0015
13 45 0025
13 45 0036
10 05 0000
10 05 0005
10 05 0015
10 05 0021
00010
WATER
TEMP
CENT
16.2
15.9
15.9
26.6
26.5
26.3
25.7
24.6
22.3
22.3
21.4
20.7
00300 00077 00094
DO TRANSP CNDUCTVY
SECCHI FIELD
MG/L INCHES MICkOMHO
110
110
105
187
181
168
189
175
162
162
112
85
16.2
15.9
15.9
26.6
26.5
26.3
25.7
24.6
22.3
22.3
21.4
20.7
9.2
9.3
7.8
7.4
7.0
5.5
7.6
8.0
7.8
84
120
77
11EPALES
3
00400
PH
SU
5.10
5.10
5.20
4.10
4.10
4.10
4.30
4.30
4.40
4.70
5.70
6.00
00410
T ALK
CAC03
MG/L
10K
10K
10K
10K
10K
10K
10
11
10K
10K
10K
10K
2111202
0018
00610
NH3-N
TOTAL
MG/L
0.050
0.040
0.050
0.140
0.120
0.100
0.130
0.130
0.260
0.170
0.200
o.iao
FEET DEPTH
00625
TOT KJEL
N
MG/L
0.200
0.200K
0.200K
0.500
0.400
0.300
0.300
0.400
0.900
0.500
0.500
0.500
00630
N02&N03
N-TOTAL
MG/L
0.450
0.450
0.460
0.310
0.320
0.320
0.330
0.330
0.300
0.280
0.360
0.370
00671
PHOS-OIS
ORTHO
MG/L P
0.004
0.004
0.003
0.003
0.002
0.003
0.002
0.003
0.004
0.003
0.004
0.004
00665 32217
DATE TIME DEPTH PHOS-TOT CHLRPHYL
FROM OF A
TO DAY FEET MG/L P UG/L
73/04/24 09 05 0000
09 05 0006
09 05 0014
73/07/28 13 45 0000
13 45 0005
13 45 0015
13 45 0025
13 45 0036
73/10/05 10 05 0000
10 05 0005
10 05 0015
10 05 0021
0.005
0.006
O.OOb
0.005
0.005
0.005
0.005
0.005
0.011
0.009
0.011
0.020
0.5K
11.9
1.4
K VALUE KNOWN TO BE
LESS THAN INDICATED
-------
STORET RETRIEVAL DATE 75/03/25
540202
39 41 18.0 079 53 46.0
LAKE LYNN RESERVOIR
54061 WEST VIRGINIA
DATE
FROM
TO
73/04/24
73/07/28
73/10/05
00010
TIME DEPTH WATER
OF TEMP
DAY FEET
09
09
09
09
09
09
09
13
13
13
13
13
13
10
10
10
10
10
10
40
40
40
40
40
40
40
05
05
05
05
05
05
30
30
30
30
30
30
0000
0006
0015
0022
0030
0042
0054
0000
0005
0015
0025
0045
0070
0000
0005
0015
0020
0040
0055
CENT
16
16
15
14
14
11
11
26
26
26
25
22
18
22
22
22
21
19
19
.3
.3
.9
.9
.0
.7
.2
.3
.4
.0
.7
.7
.7
.3
.3
.3
.4
.9
.8
HEP ALES
00300
00
MG/L
9.1
9.3
10.2
10.2
10.2
10.2
7.5
7.6
6.8
6.3
5.3
7.4
7.4
7.8
8.0
8.0
00077 00094
TRANSP CNOUCTVY
SECCHI FIELD
INCHES MICHOMHO
60 100
85
110
90
95
100
110
84 191
198
196
240
160
105
74 166
167
166
138
100
107
3
00400
PH
SU
5.20
5.20
4.60
4.90
4.80
• 4.60
4.50
4.00
4.00
4.00
3.90
3.90
4.70
4.30
4.30
4.90
5.10
6.20
6.20
00410
T ALK
CAC03
MG/L
10K
10K
10K
10*
10K
10K
10K
10K
10K
10K
10K
10K
10
10K
10K
10K
10K
10K
10K
2111202
0058
00610
NH3-N
TOTAL
MG/L
0.050
0.040
0.040
0.040
0.030
0.060
0.070
0.150
0.130
0.140
0.140
0.160
0.250
0.330
0.190
0.150
0.120
0.090
0.090
FEET DEPTH
00625
TOT KJEL
N
MG/L
0.200K
0.200K
0.200K
0.200K
0.200K
0.200K
0.200K
0.500
0.400
0.300
0.400
0.400
0.500
0.700
0.600
0.600
0.700
0.400
0.300
00630
N02&N03
N-TOTAL
MG/L
0.460
0«460
0.460
0.490
0.510
0.510
0.500
0.290
0.290
0.290
0.290
0.290
0.420
0.360
0.290
0.270
0.290
0.310
0.310
00671
PHOS-OIS
ORTHO
MG/L P
0.002K
0.002K
0.002K
0.002
0.003
0.004
0.005
0.004
0.002
0.003
0.002K
0.005
0.002
0.003
0.003
0.003
0.002
0.004
0.005
K VALUE KNOWN TO BE
LESS THAN INDICATED
-------
STORE! RETRIEVAL DATE 75/03/35
00665
DATE TIME DEPTH PMOS-TUT
FROM OF
TO DAY FEET MG/L P
73/04/24 09 40 0000 0.006
09 40 0006 U.005
09 40 0015 0.005
09 40 0032 0.006
09 40 0030 0.005
09 40 0042 0.007
09 40 0054 0.005
73/07/23 13 05 0000 0.005
13 05 0005 u.004
13 05 0015 0.006
13 05 0025 0.009
13 05 0045 0.005
13 05 0070 0.006
73/10/05 10 30 0000 u.007
10 30 0005 0.006
10 30 0015 0.007
10 30 0020 0.009
10 30 0040 0.026
10 30 0055 0.030
32217
CHLRPHYL
A
UG/L
0.5K
15.9
2.2
K VALUE KNOWN TO BE
LESS THAN INDICATED
540202
39 41 18.0 079 53 46.0
LAKE LYNN RESERVOIR
54061 WEST VIRGINIA
HEPALES
3
2111202
0058 FEET
DEPTH
-------
STORE! RETRIEVAL DATE 75/03/25
540203
39 42 55.0 079 51 13.0
LAKE LYNN RESERVOIR
54061 HEST VIRGINIA
DATE
FROM
TO
73/04/24
73/07/28
73/10/05
TIME DEPTH
OF
DAY
10
10
10
10
10
10
10
10
10
10
10
10
10
10
10
10
10
10
10
FEET
20
20
20
20
20
20
20
30
30
30
30
30
30
55
55
55
55
55
55
0000
0006
0015
0022
0030
0040
0051
0000
0005
0015
0025
0045
0077
0000
0005
0020
0035
0055
0074
00010
WATER
TEMP
CENT
15.7
15.6
15.2
15.1
14.3
13.2
11.1
26.6
26.5
26.5
25.2
21.3
13.2
22.7
22.7
21.3
20.3
19.8
15.2
00300
DO
MG/L
9.5
9.8
9.7
10.1
10.6
8.7
7.6
7.6
4.6
4.4
2.2
7.4
7.2
7.6
7.6
0.2
00077 00094
TRANSP CNDUCTVY
SECCHI FIELD
INCHES MICROMHO
120
144
108
95
95
80
70
70
60
60
161
162
162
211
89
159
167
167
121
97
95
168
11EPALES
3
00400
PH
SU
6.30
5.50
5.50
5.40
5.40
5.40
5.30
4.10
4.10
4.00
3.90
4.30
3.90
4.40
4.50
5.40
5.90
5.90
5. BO
00410
T ALK
CAC03
MG/L
10K
10K
10K
10K
10K
10K
10K
10K
10K
10K
10K
10K
10K
10K
10K
10K
10K
10K
10K
2111802
0055
00610
NH3-N
TOTAL
MG/L
0.040
0.050
0.030
0.030
0.040
0.030
0.040
0.100
0.080
0.080
0.200
0.190
0.720
0.180
0.160
0.120
0.110
0.110
1.770
FEET DEPTH
00625
TOT KJEL
N
MG/L
0.300
0.400
0.500
0.200K
0.200
0.200
0.500
0.400
0.200
0.200K
0.400
0.400
1.000
0.400
0.300
0.300
0.300
0.400
2.300
00630
N02&N03
N-TOTAL
MG/L
0.500
0.490
0.500
0.510
0.520
0.510
0.500
0.330
0.320
0.330
0.290
0.360
0.220
0.260
0.260
0.310
0.380
0.370
0.030
00671
PHOS-OIS
ORTHO
MG/L P
0.002
0.002K
0.002K
0.002K
0.002K
0.002
0.002
0.002K
0.002K
0.004
0.003
0.003
0.002
0.004
0.003
0.003
0.005
0.005
0.007
K VALUE KNOWN TO BE
LESS THAN INDICATED
-------
STORET RETRIEVAL DATE 75/03/25
DATE
FROM
TO
73/04/24
00665
TIME DEPTH PHOS-TOT
OF
DAY FEET MG/L P
73/07/28
73/10/05
10
10
10
10
10
10
10
10
10
10
10
10
10
10
10
10
10
10
10
20
20
20
20
20
20
20
30
30
30
30
30
30
55
55
55
55
55
55
0000
0006
0015
0022
0030
0040
0051
0000
0005
0015
0025
0045
0077
0000
0005
0020
0035
0055
0074
0
0
0
0
0
0
0
0
0
0
0
0
c
0
0
0
0
0
0
.006
.005
.004
.010
.005
.006
.007
.006
.004
.004
.004
.009
.004
.008
.007
.009
.017
.019
.044
32217
CHLRPHYL
A
UG/L
0.5K
8.1
1.6
K VALUE KNOWN TO BE
LESS THAN INDICATED
540203
39 *»2 55.0 079 51 13.0
LAKE LYNN RESERVOIR
54061 WEST VIRGINIA
11EPALES
3
2111202
0055 FEET
DEPTH
-------
APPENDIX E
TRIBUTARY and WASTEWATER
TREATMENT PLANT DATA
-------
STORE! RETRIEVAL DATE 75/03/25
DATE
FROM
TO
73/07/29
73/08/16
73/09/15
73/10/27
73/11/18
73/12/27
74/01/12
74/02/03
74/02/28
74/03/14
74/03/30
74/04/30
74/05/20
74/06/22
00630
TIME DEPTH N02&N03
OF N-TOTAL
DAY FEET MO/L
09 25
10 13
09 50
09 40
12 55
11 50
10 20
13 00
11 30
15 00
10 25
12 50
15 10
13 30
0.310
0.350
0.252
0.220
0.430
0.616
0.588
0.520
0.500
0.504
0.528
0.440
0.360
0.360
00625
TOT KJEL
N
MG/L
0.430
0.240
0.290
0.300
0.100K
0.200
0.500
0.100K
0.100K
0.100
0.500
0.400
0.800
0.300
00610
NH3-N
TOTAL
MG/L
0.189
0.154
0.154
0.110
0.040
0.100
0.068
0.035
0.030
0.050
0.050
0.065
0.082
0.040
00671
PHOS-OIS
ORTHO
MG/L P
0.013
0.005K
0.005K
0.014
0.005K
0.005K
0.005K
0.005
0.005K
0.005*
0.005K
0.005K
0.005K
0.005K
11EPALES
4
00665
PHOS-TOT
MG/L P
0.010
0.010
0.010
0.010
0.020
0.005K
0.010
0.005K
0.005
0.005
0.005K
5402A1
39 43 13.0 079 51 29.0
CHEAT RIVER
54089 7.5 LAKE LYNN
0/LAKE LYNN
bELO UAM .5 MI SSE OF VILLAGE OF LK LYNN
2111204
0000 FEET DEPTH
K VALUE KNOWN TO BE
LESS THAN INDICATED
-------
STORET RETRIEVAL DATE 75/03/25
S402A2
39 39 28.0 079 50 58.0
CHEAT RIVER
54 7.5 LAKE LYNN
I/LAKE LYNN
BANK AT MONT CHATEAU STATE PARK
11EPALES 2111204
4 0000 FEET DEPTH
OATE
FROM
TO
73/07/29
73/00/18
73/09/15
73/10/27
73/11/18
73/12/27
74/01/12
74/02/03
74/02/28
74/03/14
7WG3/30
74/04/30
74/05/20
74/06/22
00630 00625
TIME DEPTH N02«kN03 TOT KJEL
OF N-TOTAL N
DAY FEET
13
10
09
10
13
12
11
13
12
15
14
13
15
14
25
05
07
40
45
50
10
50
30
45
05
40
50
30
MG/L
0
0
0
0
0
0
0
0
0
0
0
0
0
0
.273
.370
.154
.180
.440
.552
.520
.520
.520
.450
.490
.352
.368
.320
MG/L
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
840
250
220
900
150
500
700
100K
300
100
200
200
400
200
00610 00671 00665
NH3-N PtlOS-DIS PHOS-TOT
TOTAL ORTHO
MG/L MG/L
0.046
0.034
0.160
0.110
0.024
0.044
0.052
0.025
0.030
0.020
0.055 '
0.025
0.075
0.030
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
p
006
009
005K
012
005K
005K
005K
005
005K
005K
005K
005K
005K
005K
MG/L P
0
0
0
0
0
0
0
0
0
0
0
0
.006
.020
.010
.025K
.090
.025
.005K
.030
.005K
.020
.010
.005K
K VALUE KNOWN TO BE
LESS THAN INDICATED
-------
STORET RETRIEVAL DATE 75/03/25
5402B1
39 43 16.0 079 49 58.0
RJbLES RUN
54 7.5 LAKE LYNN
T/LAKE LYiMN
BANK ALONG RO NEAR MOUTH 3 E OF LK LYNN
11EPALES 211120H
4 0000 FEET DEPTH
DATE
FROM
TO
73/07/29
73/08/18
73/09/15
73/10/27
73/11/lfa
73/12/27
74/01/12
74/02/03
74/02/28
7W03/14
74/03/30
7
-------
STORET RETRIEVAL DATE 75/03/35
5402C1
39 40 44.0 079 51 23.0
COLES RUN
54 7.5 LAKE LYNN
T/LAKE LYNN
SEC RO BROG AT SUNSET BEACH
11EPALES 2111204
4 0000 FEET
DATE
FROM
TO
73/07/29
73/08/18
73/09/15
73/10/27
73/11/18
73/12/27
74/01/12
74/02/03
74/02/28
74/03/1^
74/03/30
74/04/30
74/05/20
74/06/22
00630 00625
TIME DEPTH N02fcN03 TOT KJEL
OF N-TOTAL N
DAY FEET
13
09
oa
10
14
12
13
13
12
15
13
13
13
14
05
50
50
25
00
20
00
30
05
25
50
25
40
05
MG/L
0
0
0
0
0
1
0
0
0
1
1
0
0
0
.273
.231
.500
.180
.470
.010
.980
.800
.672
.180
.060
.680
.850
.660
MG/L
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
1.
0.
1.
0.
520
230
360
350
200
300
500-
200
300
900
000
600
200
400
00610 00671 00665
NH3-N PHOS-DIS PHOS-TOT
TOTAL ORTHO
MG/L
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
078
107
132
078
056
156
168
120
110
3*5
270
210
400
370
MG/L
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
p
005K
006
005K
013
005K
005K
005K
010
005
005K
005K
005K
005K
005K
MG/L P
0.010
0.010
0.010
0.005
0.015
0.025
0.011
0.02C
0.005K
0.010
0.015
0.010
0.015
DEPTH
K VALUE KNOWN TO BE
LESS THAN INDICATED
-------
STORE! (RETRIEVAL DATE 75/03/25
S402D1
39 39 30.0 079 51 55.0
WHITES RUN
54 7.5 LAKE LYNN
T/LAKE LYNN
SEC H*Y ttRDG .75 MI S OF ICES FERRY BRDG
11EPALES 2111204
4 0000 FEET DEPTH
DATE
FROM
TO
73/07/29
73/08/18
73/09/15
73/10/27
73/11/18
73/12/27
74/01/12
74/02/03
74/02/28
74/03/14
74/03/30
74/04/30
74/05/20
74/06/22
00630 00625
TIME DEPTH N02S.N03 TOT KJEL
OF N-TOTAL N
DAY FEET
13
10
09
16
13
11
13
13
12
14
14
13
16
15
45
15
25
00
30
15
20
45
40
25
25
55
00
00
MG/L
0
u
1
1
0
1
1
0
0
0
u
0
0
0
.780
.890
.160
.120
.970
.120
.360
.520
.640
.610
.640
.500
.520
.610
MG/L
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
1.
0.
1.
0.
620
170
420
300
500
100
800
100K
300
300
200
500
200
200
00610 00671 00665
NH3-N PHOS-DIS PHOS-TOT
TOTAL ORTHO
MG/L
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
025
038
054
033
040
020
072
025
065
045
080
050
140
050
MG/L
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
p
052
100
110
390
060
009
024
010
065
035
050
110
040
030
MG/L P
0.090
0.175
U.180
0.680
0.095
0.040
0.040
0.010
0.140
0.090
0.130
0.118
0.070
0.075
K VALUE KNOWN TO BE
LESS THAN INDICATED
-------
RETRIEVAL DATE 75/03/25
5402E1
39 40 35.0 079 53 47.0
UNNAMED STREAM
54 7.5 N MORGANTOtfN
T/LAKE LYNN
SEC HrtY 8RDG .25 MI W OF CANYON
11EPALES 2111204
4 0000 FEET DEPTH
DATE
FKOM
TO
73/07/29
73/06/18
73/09/15
73/10/27
73/11/18
/J/12/27
/W01/12
/H/02/03
W02/28
7W03/14
74/03/30
74/04/30
74/05/20
74/06/22
00630 00625
TIME DEPTH N02^N03 TOT KJEL
OF N-TOTAL N
DAY FEET
14
09
09
11
14
13
13
14
12
16
14
14
16
15
00
30
35
15
15
07
30
05
50
00
35
05
10
10
MG/L
0
0
0
0
0
0
0
0
0
0
.630
.200
.288
.124
.044
.040
.046
.045
.064
.027
MG/L
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
1.
0.
0.
0.
660
840
850
700
600
400
700
400
500
800
000
700
700
345
00610 00671 00665
NH3-N PHOS-DIS PHOS-TOT
TOTAL ORTHO
MG/L
0.
0.
0*
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
520
600
820
384
450
300
352
315
315
330
300
375
460
345
MG/L
0.
0.
0.
0.
0.
0.
1.
1.
0.
0.
0.
0.
0.
0.
p
510
357
400
553
216
220
000
000
800
760
680
670
101
490
MG/L P
0.530
0.470
0.460
0.700
0.220
0.345
1.050
1.050
0.800
0.770
0.750
0.810
0.620
0.580
-------
STORE! RETRIEVAL DATE 75/03/25
5402AA PD5402AA P000950
39 22 00.0 079 40 30.0
KOrfLESBERG
54089 PRESTON COUNTY
T/LAKE LYNN
CHEAT RIVER
11EPALES 2141204
4 0000 FEET DEPTH
DATE
FROM
TO
73/09/12
73/10/12
73/11/13
73/12/18
7WU1/15
74/02/13
74/03/12
74/04/10
7^/05/14
7^/06/11
7^/07/17
7^/08/12
00630 00625
TIME DEPTH N02&N03 TOT KJEL
OF N-TOTAL N
DAY FEET
15
15
15
15
15
15
15
15
15
15
15
15
00
45
20
00
05
40
30
40
30
40
45
20
MG/L
0
0
0
0
u
0
0
0
0
0
0
0
.015
.010K
.090
.740
.200
.080
.040
.040
.240
.040
.160
.120
MG/L
8.600
6.650
2.300
1.300
2.000
l.OOOK
1.000
l.OOOK
3.000
5.100
2.800
6.300
00610 00671 00665
NH3-N PHOS-OIS PHOS-TOT
TOTAL ORTHO
MG/L
0
0
0
0
0
0
0
0
0
0
0
.140
.180
.110
.058
.066
.050K
.110
.140
.130
.063
.050K
MG/L P
0.830
1.400
0.090
0.170
0.140
0.120
0.050K
0.057
0.280
0.180
0.290
0.056
50051 50053
FLOW CONDUIT
RATE FLOW-MGD
MG/L P INST
1.600
3.200
0.250
0.220
0.260
0.160
0.260
0.320
0.530
O.<*50
0.655
1.300
0
0
0
0
0
0
0
0
0
0
0
MGD MONTHLY
.080
.080
.080
.080
.080
.080
.080
.080
.080
.080
0.080
.080
K VALUE KNOWN TO BE
LESS THAN INDICATED
------- |