U.S. ENVIRONMENTAL PROTECTION AGENCY
NATIONAL EUTROPHICATION SURVEY
WORKING PAPER SERIES
REPORT
ON
OTOLAND LAKE
CLINTON, PULASKI, RUSSELL,
AND WAYNE COUNTIES
IOTUCKY
EPA REGION IV
WORKING PAPER No, 351
CORVALLIS ENVIRONMENTAL RESEARCH LABORATORY - CORVALLIS, OREGON
and
ENVIRONMENTAL MONITORING & SUPPORT LABORATORY - LAS VEGAS, NEVADA
•&G.P.O. 699-440
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REPORT
ON
OJIWAND LAKE
CLINTON, PULASKI, RUSSELL,
AND WAYNE COUNTIES
KENTUCKY
EPA REGION IV
WORKING PAPER No, 351
WITH THE COOPERATION OF THE
KENTUCKY DEPARTMENT FOR I^ATURAL RESOURCES AND ENVIRONMENTAL CONTROL
AND THE
KENTUCKY NATIONAL GUARD
JUNE, 1977
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i
CONTENTS
Page
Foreword ii
List of Kentucky Reservoirs iv
Lake and Drainage Area Map v, vi
Sections
I. Conclusions 1
II. Lake and Drainage Basin Characteristics 4
III. Lake Water Quality Summary 6
IV. Nutrient Loadings 11
V. Literature Reviewed 17
VI. Appendices 18
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11
FOREWORD
The National Eutrophication Survey was initiated in 1972 in
response to an Administration commitment to investigate the nation-
wide threat of accelerated eutrophication to freshwater lakes and
reservoirs.
OBJECTIVES
The Survey was designed to develop, in conjunction with state
environmental agencies, information on nutrient sources, concentrations,
and impact on selected freshwater lakes as a basis for formulating
comprehensive and coordinated national, regional, and state management
practices relating to point-source discharge reduction and non-point
source pollution abatement in lake watersheds.
ANALYTIC APPROACH
The mathematical and statistical procedures selected for the
Survey's eutrophication analysis are based on related concepts that:
a. A generalized representation or model relating
sources, concentrations, and impacts can be constructed.
b. By applying measurements of relevant parameters
associated with lake degradation, the generalized model
can be transformed into an operational representation of
a lake, its drainage basin, and related nutrients.
c. With such a transformation, an assessment of the
potential for eutrophication control can be made.
LAKE ANALYSIS
In this report, the first stage of evaluation of lake and water-
shed data collected from the study lake and its drainage basin is
documented. The report is formatted to provide state environmental
agencies with specific information for basin planning [§303(e)], water
quality criteria/standards review [§303(c)], clean lakes [§314(a,b)],
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.
ACKNOWLEDGEMENT
The staff of the National Eutrophication Survey (Office of
Research & Development, U. S. Environmental Protection Agency)
expresses sincere appreciation to the Kentucky Department for
Natural Resources and Environmental Protection for professional
involvement, to the Kentucky National Guard for conducting the
tributary sampling phase of the Survey, and to those Kentucky
wastewater treatment plant operators who voluntarily provided
effluent samples.
Harold Snodgrass, former Director, and Mercer M. Peters of
the Division of Water Quality provided invaluable lake documen-
tation and counsel during the Survey; and the staff of the Divis-
ion reviewed the preliminary reports and provided critiques most
useful in the preparation of this Working Paper series.
Major General Richard L. Frymire, the Adjutant General of
Kentucky, and Project Officers Lt. Colonel Thomas Buyher, Jr.,
and Lt. Colonel David B. May, who directed the volunteer efforts
of the Kentucky National Guardsmen, are also gratefully acknow-
ledged for their assistance to the Survey.
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iv
NATIONAL EUTROPHICATION SURVEY
STUDY RESERVOIRS
STATE. OF KENTUCKY
NAME
Barkley
Barren River
Cumberland
Dale Hollow
Herrington
Kentucky
COUNTY
Lyon, Trigg, KY;.
Cheatharo, Montgomery,
Stewart, TN
Allen, Barren
Clinton, Pulaski, Russell,
Wayne
Clinton, Cumberland, KY;
Clay, Overton, Pickett, TN
Boyler, ^arrard, Mercer
CaVloway, Livingston, Lyon,
Marshall, Trigg, KY;
Benton, Decatur, Henry,
Houston, Humphreys, Perry,
Stewart, TN
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CUMBERLAND LAKE
Tributary Sampling Site
X Lake Sampling Site
• Sewage Treatment Facility:
KENTUCKY
TENNESSEE
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Columbia
CUMBERLAND LAKE
Tributary Sampling Site
X Lake Sampling Site
Sewage Treatment Facility
Drainage Area Boundary
V
V T f K
TO JO 30 * SO Mi.
Scale
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CUMBERLAND LAKE
STORE! NO. 2101
CONCLUSIONS
A. Trophic Condition:
Survey data indicate that Cumberland Lake is mesotrophic;
i.e., moderately supplied with nutrients and moderately pro-
ductive. Whether nutrient enrichment is beneficial or deleterious
depends on the actual or potential effect on the uses of the
lake. In this regard, personnel of the Kentucky Department for
Natural Resources and Environmental Protection have indicated
there is no known impairment of the beneficial uses of Cumberland
Lake.
This water body ranked second in overall trophic quality
when the five Kentucky reservoirs sampled in 1973 were compared
using a combination of six parameters*. One of the reservoirs
had less median total phosphorus, two had less median dissolved
phosphorus, one had less median inorganic nitrogen, one had less
mean chlorophyll! a_, and one had greater mean Secchi disc trans-
parency. Marked depression of dissolved oxygen with depth occurred
at six of the seven sampling stations in October.
Survey limnologists did not observe macrophytes or surface
concentrations of algae during any of the sampling visits; and
in a summary report (Anonymous, 1976), it is concluded that this
is a mesotrophic reservoir of high water quality which provides
a fine sport fishery.
* See Appendix A.
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2
B. Rate-Limiting Nutrient:
The algal assay results indicate the lake was phosphorus
limited at the time the samples were collected (05/29/73). The
lake data also indicate phosphorus limitation; at all sampling
times the mean inorganic nitrogen to orthophosphorus ratios were
greater than 30 to 1, and phosphorus limitation would be expected.
C. Nutrient Controllability:
1. Point sources—The phosphorus contributions of the listed
point sources accounted for less than 5% of the total input to
Cumberland Lake. Somerset contributed 3.1%; Monticello, 1.2%;
Russell Springs, 0.5%; and Williamsburg, 0.1%. However, the
phosphorus export rates of the Cumberland River and Beaver Creek,
were significantly higher than the rates of the other tributaries
(see page 15). For the Cumberland River, it is likely that point
«
sources beyond the 40-kilometer limit of the Survey* contributed,
to the phosphorus inputs to Cumberland Lake.
The phosphorus loading of 1.96 g/m2 measured during the
sampling year is over 1.6 times that proposed by Vollenweider
(Vollenweider and Dillon, 1974) as a eutrophic loading (see
page 16). For this reason, all phosphorus inputs to the reser-
voir should be minimized to the greatest possible extent to slow>
the trend toward a eutrophic condition.
2. Non-point sources—The phosphorus load from non-point
sources accounted for over 95% of the total reaching Cumberland
Lake. About 50% of the phosphorus input can be attributed to the
* See Working Paper No. 175, "...Survey Methods, 1973-1976".
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3
Cumberland River after accounting for the point-source load from
the town of Williamsburg. As discussed above, part of the phos-
phorus load of the Cumberland River may be due to distant point
sources rather than non-point source contributions.
Beaver Creek had an apparent phosphorus export rate of 71
kg/km2/yr, which is also much higher than would be expected from
non-point sources and could have resulted from an underestimation
of the contribution of the Monticello waste treatment facility
or to unidentified point sources in that drainage basin.
Among the other tributaries, substantial phosphorus con-
tributions came from the South Fork of the Cumberland River
(12.9%) and Rockcastle Creek (10.2%). The 17 additional listed
tributaries collectively contributed 15.9% of the total. The
ungaged tributaries contributed an estimated 5.3% of the total
phosphorus input to the lake.
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II.
LAKE AND DRAINAGE BASIN CHARACTERISTICS1"
J.rL
A. Morphometry :
1. Surface area: 203.36 kilometers2.
2. Mean depth: 24.2 meters.
3. Maximum depth: >56.7 meters.
4. Volume: 4,927.800 x 10s m3.
5. Mean hydraulic retention time: 226 days.
B.
Tributary and Outlet:
(See Appendix C for flow data)
1. Tributaries -
Name
Drainage
area (km2)*
Cumberland River 5,180.0
Indian Creek 22.5
Williams Creek 21.0
Otter Creek 174.3
Beaver Creek 238.3
Meadow Creek 48.2
Lily Creek 26.4
Horse Creek 43.0
Wolf Creek 43.0
White Oak Creek 59.3
Fishing Creek Arm 365.2
Sinking Creek (M-l) 42.2
Pitman Creek 192.2
Buck Creek 758.9
Rockcastle Creek 1,921.8
Laurel River 733.0
Beaver Creek (S-l) 55.7
South Fork, Cumberland River 2,805.0
Little S. Fk., Cumberland River 308.2
Sinking Creek (V-l) 111.4
Minor tributaries &
immediate drainage - 1,640.5
Totals 14,790.1
Mean flow
(m3/sec)*
89.47
0.30
0.28
2.
3.
.39
.28
0.64
0.35
0.57
0.57
0.80
5.07
0.56
2.
11.
94
73
30.88
11.48
0.75
55.07
4.26
1.51
29.94
252.84**
t Table of metric conversions—Appendix B.
tt At maximum power pool (el. 220 m.): Jett, 1974; Anonymous, 1976.
* For limits of accuracy, see Working Paper No. 175.
** Sum of inflows adjusted to equal outflow.
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5
Drainage Mean flow
Name area (km2)* (m3/sec)*
2. Outlet -
Cumberland River 14,993.5** 252.84
C. Precipitation***:
1. Year of sampling: 150.0 centimeters.
2. Mean annual: 120.6 centimeters.
* For limits of accuracy, see Working Paper No. 175.
** Includes area of lake.
*** See Working Paper No. 175.
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6
III. WATER QUALITY SUMMARY
Cumberland Lake was sampled three times in 1973 by means of a
pontoon-equipped Huey helicopter. Each time, samples for physical
and chemical parameters were collected from seven 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 to surface)
sample was composited from the stations for phytoplankton identi-
fication and enumeration; and during the first visit, two 18.9-
liter depth-integrated samples were 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 56.7 meters at station 1, 44.2 meters at station 2, 30.5 meters
at station 3, 39.6 meters at station 4, 40.2 meters at station 5,
36.3 meters at station 6, arid 25.6 meters at station 7.
The sampling results are presented in full in Appendix D and are
summarized in the following table.
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PARAMETER
TEMP (C)
DISS OXY CMG/L)
CNDCTVY
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)
IMORG N (MG/L)
TOTAL N (MG/L)
CHLRPYL A (UG/L)
SECCHI (METERS)
A. SUMMARY OF PHYSICAL AND
1ST SAMPLING ( 5/29/73)
7 SITES
CHEMICAL CHARACTERISTICS FOR LAKE CUMBERLAND
STORE! CODE 2101
2ND SAMPLING ( 8/21/73)
7 SITES
3KJ SAMPLING (10/25/73)
7 SITES
RANGE
9.4
8.0
„**.»
7.3
25.
0.01?
0.002
0.220
0.030
0.200
0.260
0.420
1.1
0.1
- 19.6
9.8
-*«*.*»»«
7.7
56.
- 0.069
- 0.025
- 0.420
- 0.140
- 0.500
- 0.480
- 0.740
2.4
1.8
MEAN
15.6
9.0
>.......<
7.5
38.
0.023
0.007
0.303
0.051
0.263
0.354
0.566
1.8
1.1
MEDIAN
16.6
9.0
>««»»»
7.5
36.
0.018
0.006
0.300
0.040
0.300
0.340
0.570
1.8
1.0
RANGE
9.7
2.2
65.
5.9
27.
0.007
0.004
0.050
0.040
0.200
0.090
0.260
3.6
1.0
- 28.1
9.1
- 205.
8.8
59.
- 0.056
- 0.022
- 0.520
- 0.080
- 0.600
- 0.560
- 0.760
8.5
2.4
MEAN
20.9
5.8
135.
7.0
38.
0.017
0.007
0.273
0.055
0.265
0.328
0.538
7.1
1.6
MEDIAN
21.5
5.2
136.
6.9
36.
0.013
0.006
0.340
0.050
0.200
0.405
0.580
7.6
1.5
RANGE
10.7
0.1
95.
6.7
26.
0.008
0.005
0.100
0.030
0.200
0.140
0.300
1.7
1.5
- 23.2
7.2
- 177.
7.6
53.
- 0.054
- 0.013
- O.<*40
- 0.230
- 0.800
- 0.480
- 0.920
3.9
3.0
MEAN
19.3
4.1
130.
7.1
39.
0.019
0.006
0.206
0.047
0.260
0.253
0.466
2.6
2.3
MEDIAN
21.4
5.8
130.
7.3
39.
0.01S
0.008
0 . 1 30
0.040
0.200
0. 1BO
0.^20
2.4
2.7
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8
B. Biological characteristics:
1. Phytoplankton -
Sampling
Date
05/29/73
08/21-22/73
10/25/73
2. Chlorophyll a -
Sampling
Date
05/29/73
08/21-22/73
Dominant
Genera
1.
2.
3.
4.
5.
1.
2.
3.
4.
5.
1.
2.
3.
4.
5.
Flagellates
Fragilaria sj).
Dinobryon sj3.
CryjDtomonas sp_.
Stephanodiscus sj),
Other genera
Total
Anomoeoneis sp.
Flagellates
Cosmarium sja.
Cyclotella S£.
Fragilaria SJD.
Other genera
Total
Anomoeoneis sp.
Flagellates
Synedra sp.
Fragilaria sp.
Cyclotella sjx
Other genera
Algal Units
per ml
447
394
105
79
66
79
Total
Station
Number
1
2
3
4
5
6
7
1
2
3
4
5
6
7
1,170
5,132
572
248
133
57
173
6,315
628
107
107
92
61
154
1,149
Chlorophyll a
(ufl/D
1.1
1.8
2.4
2.3
2.3
1.2
1.2
7.5
8.0
7.9
7.6
8.5
6.4
3.6
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c.
Sampling
Date
10/25/73
Limiting Nutrient Study:
1. Autoclaved, filtered,
a. Stations 1,2, and
Ortho
Spike (mg/1) Cone.
Control
0.050 P
0.050 P + 1.0 N
1.0 N
b. Stations 4, 5, 6,
Ortho
Spike (mg/1) Cone.
Control
0.050 P
0.050 P + 1.0 N
1.0 N
2. Discussion -
The control yields
Station
Number
1
2
3
4
5
6
7
and nutrient
3 -
P
(mg/1)
0.004
0.054
0.054
0.004
and 7 -
P
(mg/1)
0.024
0.074
0.074
0.024
spiked -
Inorganic N
Cone, (mg/1)
0.348
0.348
1.348
1.348
Inorganic N
Cone, (mg/1)
0.296
0.296
1.296
1.296
Chlorophyll a
(WJ/I)
3.9
3.6
2.5
1.7
1.7
2.3
2.4
Maximum yield
(mg/1 -dry wt. )
0.1
4.9
15.4
0.1
Maximum yield
(mg/1 -dry wt.)
0.1
4.4
16.7
0.1
of the assay alga, Selenastrum capri-
cornutum, indicate the potential primary productivity of
Cumberland Reservoir was low at the time the samples were
collected (05/29/73). In both assays, the significant
increases in yield with the addition of phosphorus alone
indicate phosphorus limitation. Note that in neither assay
did the addition of nitrogen alone result in an increase in
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10
yield.
The lake data also indicate phosphorus limitation. The
mean inorganic nitrogen to orthophosphorus ratios were 32 to
1 or greater at all sampling times.
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11
IV. NUTRIENT LOADINGS
(See Appendix E for data)
For the determination of nutrient loadings, the Kentucky National
Guard collected monthly near-surface grab samples from each of the
tributary sites indicated on the map (page v), except for the months
of May, 1973, and January and February, 1974, when two samples were
collected at most of the sites. Sampling was begun in March, 1973, and
was completed in March, 1974.
Through an interagency agreement, stream flow estimates for the
year of sampling and a "normalized" or average year were provided by
the Kentucky District Office of the U.S. Geological Survey for the
tributary sites nearest the lake.
Except for Sinking Creek (M-l), nutrient loads for sampled tribu-
taries 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.
The nutrient loads measured at the Somerset wastewater treatment
plant exceeded the loads measured in Sinking Creek at station M-l; the
nutrient loads for this stream and the unsampled "minor tributaries and
immediate drainage" ("ZZ" of U.S.G.S.) were estimated using the means
of the nutrient exports, in kg/km2/year, at stations B-l, C-l, D-l,
F-l, H-l, J-l, K-l, L-l, N-l, P-l, Q-l, R-l, S-l, T-l, U-l, and V-l and
multiplying the means by the M-l and ZZ areas in km2.
The operators of the Monti cello, Williamsburg, and Somerset waste-
* See Working Paper No. 175.
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12
water treatment plants provided monthly effluent samples and corres-
ponding flow data. The operator of the Russell Springs treatment plant
did not participate in the sampling program, and nutrient loads were
estimated at 1.134 kg P and 3.401 kg N/capita/year.
A. Waste Sources:
1. Known municipal -
Name
Russell
Springs
Monti cello
Williamsburg
Somerset
Pop.
Served*
1,641
3,618
3,687
10,436
Mean Flow
Treatment (m3/d)
trickling 621.1**
filter
trickling 927.7
filter
trickling 923.3
f i 1 ter
act. sludge 5,659.2
Receiving
Water
Lily Creek
Elk Spring Creek/
Beaver Creek
Cumberland River
Sinking Creek (M-
2. Known industrial - None
t Anonymous, 1971.
* 1970 Census.
** Estimated at 0.3785 m3/capita/day.
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13
B. Annual Total Phosphorus Loading - Average Year:
1. Inputs -
kg P/ % of
Source y_r total
a. Tributaries (non-point load) -
Cumberland River 198,405 49.9
Indian Creek 235 0.1
Williams Creek 180 <0.1
Otter Creek 1,020 0.3
Beaver Creek (E-l) 16,810 4.2
Meadow Creek 785 0.2
Lily Creek 645 0.2
Horse Creek 440 0.1
Wolf Creek 370 0.1
White Oak Creek 530 0.1
Fishing Creek Arm 4,900 1.2
Sinking Creek (M-l) 535 0.1
Pitman Creek 4,190 1.1
Buck Creek 11,845 3.0
Rockcastle Creek 40,745 10.2
Laurel River 17,655 4.4
Beaver Creek (S-l) 205 <0.1
South Fork, Cumberland River 51,225 12.9
Little S. Fk., Cumberland River 2,465 0.6
Sinking Creek (V-l) 940 0.2
b. Minor tributaries & immediate
drainage (non-point load) - 20,835 5.3
c. Known municipal STP's -
Russell Springs 1,860 0.5
Monticello 4,695 1.2
Williamsburg 300 0.1
Somerset 12,375 3.1
d. Septic tanks* - 20 <0.1
e. Known industrial - None
f. Direct precipitation** - 3,560 0.9
Total 397,770 100.0
2. Outputs -
Lake outlet - Cumberland River 243,735
3. Net annual P accumulation - 154,035 kg.
* Estimate based on 73 shoreline dwellings; see Working Paper No. 175.
** See Working Paper No. 175.
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14
C. Annual Total Nitrogen Loading - Average Year:
1. Inputs -
kg N/ % of
Source yr total
a. Tributaries (non-point load) -
Cumberland River 3,748,075 37.3
Indian Creek 15,680 0.2
Williams Creek 13,565 0.1
Otter Creek 73,170 0.7
Beaver Creek (E-l) 186,655 1.9
Meadow Creek 27,120 0.3
Lily Creek 11,465 0.1
Horse Creek 21,865 0.2
Wolf Creek 19,985 0.2
White Oak Creek 28,875 0.3
Fishing Creek Arm 205,675 2.0
Sinking Creek (M-l) 22,685 0.2
Pitman Creek 131,815 1.3
Buck Creek 408,005 4.1
Rockcastle Creek 2,319,940 23.1
Laurel River 573,855 5.7
Beaver Creek (S-l) 14,325 0.1
S. Fork, Cumberland River 990,995 9.9
Little S. Fk., Cumberland R. 69,195 0.7
Sinking Creek (V-l) 22,615 0.2
b. Minor tributaries & immediate
drainage (non-point load) - 881,935 8.8
c. Known municipal STP's -
Russell Springs 5,580 0.1
Monticello 10,515 0.1
Williamsburg 840 <0.1
Somerset 19,740 0.2
d. Septic tanks* - 780 <0.1
e. Known industrial - None
f. Direct precipitation** - 219,545 2.2
Total 10,044,495 100.0
2. Outputs -
Lake outlet - Cumberland R. 7,234,410
3. Net annual N accumulation - 2,810,085 kg.
* Estimate based on 73 shoreline dwellings; see Working Paper No. 175.
** See Working Paper No. 175.
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15
D. Non-point Nutrient Export by Subdrainage Area:
Tributary kg P/km2/yr kg N/km2/yr
Cumberland River 38 724
Indian Creek 10 697
Williams Creek 9 646
Otter Creek 6 420
Beaver Creek (E-l) 71 783
Meadow Creek 16 563
Lily Creek 24 434
Horse Creek 10 508
Wolf Creek 9 465
White Oak Creek 9 487
Fishing Creek Arm 13 563
Pitman Creek 22 686
Buck Creek 16 538
Rockcastle Creek 21 1,207
Laurel River 24 783
Beaver Creek (S-l) 4 257
South Fork, Cumberland River 18 353
Little S. Fk., Cumberland River 8 225
Sinking Creek (V-l) 8 203
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16
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 meso-
trophic loading would be considered one between "dangerous"
and "permissible".
Note that Vollenweider's model may not be applicable to
water bodies with short hydraulic retention times.
Total Phosphorus Total Nitrogen
Total Accumulated Total Accumulated
grams/m2/yr 1.96 0.76 49.4 13.8
Vollenweider phosphorus loadings
(g/m2/yr) based on mean depth and mean
hydraulic,retention time of Cumberland Reservoir:
"Dangerous" (eutrophic loading) 1.20
"Permissible" (oligotrophic loading) 0.60
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17
LITERATURE REVIEWED
Anonymous, 1971. Inventory of municipal waste facilities. EPA
Publ. OWP-1, Vol. 4, Wash., D.C.
Anonymous, 1976. Water quality conditions in Lake Cumberland.
Nashville Distr., U.S. Corps of Engineers, Nashville, TN.
Jett, Shelby, 1974. Personal communication (lake morphometry).
Dept. for Nat. Resources & Env. Protection, Frankfort.
Vollenweider, R. A., and P. J. Dillon, 1974. The application of
the phosphorus loading concept to eutrophication research.
Natl. Res. Council of Canada Publ. No. 13690, Canada Centre
for Inland Waters, Burlington, Ontario.
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18
VI. APPENDICES
APPENDIX A
LAKE RANKINGS
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DATA TO BE USED IN RANKINGS
LAKE
COOfc LAKE NAME
2101 LAKE ClJMriERLANU-
2102 DALE HOLLOW RESERVOIR
2103 HERRINGTON LAKE
210* KENTUCKY LAKE
2105 BARREN RIVER RESERVOIR
MEDIAN
TOTAL P
0.016
O.ulu
O.G7*
0.072
0.027
MEDIAN
iNOR'o N
0.330
0.2/0
0.550
0.520
0.460
500-
MEAN SEC
432.381
330.000
442.667
461.972
452.594
MEAN
CriLORA
3.805
3.594
14.908
9.069
6.216
15-
MIN 00
14.900
14.800
14.900
12.600
14.900
MEDIAN
DISS P
0.007
0.005
0.047
0.030
0.006
-------
PERCENT OF LAKES *ITH HIGHE* VALUES
. LAKE
CODE
2101
2102
2103
210<*
2t05
MEDIAN
LAKE NAME
LAKE CUMHtKLANU
UALE HOLLO* RESERVOIR
HtRRlN&TON LAKE
KENTUCKY LAKE
BARKEN RIVER KESUxVOIR
TOTAL
60 (
80 (
0 (
20 (
40 (
P
3)
4)
0)
1)
2)
MEDIAN
INORG
60 (
80 (
0 (
20 (
40 (
N
3)
4)
0)
1)
2)
500-
MtAN SEC
60 ( 3)
bO ( 4)
40 ( 2)
0 ( 0>
20 ( 1>
MEAN
CHLORA
60 (
80 (
0 (
20 (
40 (
15-
3)
4)
0)
1)
2)
MIN
20 I
60 <
20 '
80
20
DO
I 0)
t 3)
I 0)
( 4)
( 0)
MEDIAN
DISS
40 (
80 (
0 (
20 (
60 (
P
2)
4)
0)
1)
3)
INOE
NO
300
46C
6C
16C
220
-------
LAKES RANALD BY INOL* NOb.
RANK LAKE COUE LA*L NAME INDEX NO
UALE HOLLOW KEStKVOIR
2 2101 LAKE CUMBERLAND 300
3 21ub dAKKEN RI\/EK KESEWVOIH 220
I* 21Q4 KENIUCKY LAKE 1^0
S 2103 HEH^INGTON LAKE 60
-------
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 = 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 FLO* INFORMATION FOR KENTuCKY
2/3/75
COuE 2101 L«i\t
TOTAu OWAINAGE AKEA uF i_AKE(SU KM) 14993.5
TRIBUTARY ASEA(SQ KM)
JAN
FEB
MAR
APR
MAY
NORMALIZED FLOwS(tMS)
JUN JUL A'JG ScP
OCT
NUV
u£C
SUMMARY
TOTAL DRAINAGE AREA OF LAKE =
SUM OF SUB-DRAINAGE AREAS =
14993.5
14791.4
TOTAL FLOW IN
TOTAL FLOW OUT
2999.12
3038.48
MEAN MONTHLY FLOWS AND DAILY FLOWS(CMS)
TRIBUTARY MONTH
2101A1
MEAN FLOW DAY
FLOW DAY
FLOW DAY
FLOW
3
tt
5
6
7
e
9
10
11
12
1
2
3
73
73
73
73
73
73
73
73
73
73
74
74
74
459.58
498.38
434.95
5 30'. 94
501.77
314.03
124.06
178.48
215.94
507.44
1041.49
907.84
524.14
1
17
22
19
16
14
18
5
2
17
781.34 28
605.98
453.07
140.17
15.46
99.68
4.02
914.63 20
1112.85 17
645.62
137.05
1121.35
846.67
MEAN
2101A1
2101A2
2101B1
2101C1
21ul01
2101E1
2i01Fi
2101G1
2101H1
2101J1
2101K1
2101L1
2101*1
2101N1
2101H1
21U101
2101R1
2101S1
2101T1
2101U1
210lVi
2101Z2
14993.5
5ieo.o
28.5
21.0
17u.3
238.3
46.2
26.4
43.0
43.0
59.3
36$. 2
42.2
192.2
758.9
1921.8
733.0
55.7
2805.0
308.2
111.4
1642.1
325. U8
167.21
0.45
0.42
3.9*
5.47
1.02
0.54
0.91
0.91
1.27
8.55
0.86
4.56
18.15
58.36
23.30
1.19
109.30
7.14
2.46
41.40
322.81
185.25
0.65
0.62
5.24
7.16
1.42
0.76
1.27
1.27
1.76
11.04
1.25
7.50
29.08
70.06
26.65
1.64
128.42
9.29
3.31
50.38
431.27
211.67
0.82
0.76
6.31
8.64
1.76
0.96
1.56
1.56
2.15
13.22
1.^3
7.73
30.72
74.16
26.70
2.01
125.19
11.16
4.02
59.44
457.60
142.63
0.45
0.42
3.68
5.04
0.99
0.54
0.68
0.88
1.22
7.B2
0.88
4.84
18.60
46.52
15.46
1.13
79.77
6.57
2.32
36.16
322.25
87.36
0.31
0.28
2.41
3.28
0.68
0.37
0.59
0.59
0.82
5.01
0.59
2.32
10.25
26.22
9.80
0.79
46.72
4.25
1.56
22.23
206.58
45.08
0.14
0.13
1.22
1.67
0.31
0.17
0.28
0.26
0.40
2.63
0.27
1.44
7.19
18.55
6.12
0.37
22.77
2.21
0.76
12.74
186.41
41.68
0.13
0.12
1.05
1.44
0.28
0.15
U.25
0.25
0.34
2.24
0.25
1.36
6.54
15.80
4.53
0.34
18.97
1.87
0.65
10.34
172.48
25.51
0.06
0.05
0.54
0.76
0.13
0.07
0.12
0.12
0.17
1.22
0.12
U.<*6
1.81
7.22
1.67
0.16
8.30
1.02
0.34
6.26
121.25
12.91
U.OH
0.04
0.37
0.51
0.09
0.05
0.08
0.03
0.12
0.82
0.08
0.45
1.03
3.31
1.44
0.11
8.27
0.68
0.23
3.99
114.99
15.52
0.03
0.03
0.26
0.37
0.07
0.04
0.06
0.06
0.08
0.57
0.06
0.28
0.62
2.27
0.74
0.08
7.39
0.48
0.16
27.78
149. u3
45.51
0.15
0.14
1.19
1.64
0.31
0.18
0.28
0.28
0.40
2.b2
0.28
1.02
4.13
14.92
6.23
0.37
31.60
2.12
0.76
11.44
220.70
98. 77
0.34
0.31
2.63
3.62
0.71
0.40
0.65
0.65
0.88
5.58
0.62
3.60
13.63
35.65
16.03
0.82
78.75
4.70
1.67
25.46
252.84
89.47
0.30
0.28
2.39
3.28
0.64
0.35
0.57
0.57
0.80
5.07
0.56
2.94
11.73
3o.ttto
11.48
0.75
55.07
4.26
1.51
25.54
-------
FLO*' INFORMATION FOR KENTUCMC
a/3/75
LA
-------
TRIBUTARY FLO« INFORMATION FOR KENTUCKY
2/3/75
LAKE CODE 2101
LAKE CUMBERLAND
MEAN MONTHLY FXCwS AND UAILY FLOwS(CMS)
TRIBUTARY
2i01Dl
2101E1
2101F1
210101
MONTH
YEAR
3
4
5
6
7
8 •
9
10
11
12
1
2
3
3
4
5
6
7
8
9
10
11
12
1
2
3
3
4
5
6
7
8
9
10
11
12
1
2
3
3
4
5
6
7
a
9
10
11
12
1
2
3
73
73
73
73
73
73
73
73
73
73
74
74
74
73
73
73
73
73
73
73
73
73
73
74
74
74
73
73
73
73
73
73
73
73
73
73
74
74
74
73
73
73
73
73
73
73
73
73
73
74
74
74
MEAN FLOW DAY
8.27
3.91
7.33
3.57
2.12
0.34
0.16
0.12
3.60
5.18
12.52
5.44
5.13
11.30
5.27
10.08
4.76
2.92
0.45
0.22
0.16
4.90
7.08
16.82
7.45
6.97
2.29
1.05
2.07
0.91
0.57
0.08
0.04
0.03
0.93
1.39
3.23
1.47
1.42
1.05
0.62
0.88
0.37
0.37
0.04
0.03
0.03
0.59
0.40
1.33
0.45
0.57
1
17
22
19
lo
14
la
5
2
17
1
17
22
19
16
14
18
4
1
16
1
13
10
7
19
16
17
5
3
30
31
28
13
10
7
19
Ib
20
17
5
3
30
FLU**
3.66
0.16
O.ld
0.16
0.12
0.37
10.51
19.14
2.97
4.96
6.00
0.24
0.24
0.22
0.16
0.48
40.49
5.04
4.19
0.99
1.25
0.68
0.34
0.05
0.04
0.14
2.72
4.93
1.98
O.b4
1.16
0.91
0.08
0.31
0.03
0.03
0.02
0.06
1.02
1.13
1.64
DAY
29
20
17
28
19
16
28
20
16
20
16
FLU* DAY
5.64
2.12
2.61
14.27
3.00
3.37
2.B3
0.57
0.65
0.45
0.21
FLO»
-------
FLO* INFORMATION FOR KENTUCKY
2/3/75
LA<£ COOE 2101
CUMoEWLAND
MEAN MONTHLY fLOnS AND DAILY FLOWS(CMS)
TRIBUTARY MONTH YEAK MEAN FLOW DAT
2101HI
210U1
2101*1
2101LI
3
4
5
6
7
H
9
10
11
12
1
2
3
3
4
5
6
7
8
9
10
11
12
1
2
3
3
4
5
6
7
8
9
10
11
12
1
2
3
3
4
5
6
7
8
9
10
11
12
1
2
73
73
73
73
73
73
73
73
73
73
74
74
74
73
73
73
73
73
73
73
73
73
73
74
74
74
73
73
73
73
73
73
73
73
73
73
74
74
74
73
73
73
73
73
73
73
73
73
73
74
74
1.70
1.05
1.42
0.62
O.S9
0.07
0.06
O.OS
0.96
0.65
2.21
0.76
0.91
1.70
1.05
1.42
0.62
0.59
0.07
0.06
0.05
0.96
0.65
2.21
0.76
0.91
1.84
1.42
2.75
1.08
0.48
0.13
0.01
0.02
1.73
1.39
4.64
0.88
1.59
11.24
9.06
16.68
7.16
3.17
0.93
0.07
0.11
10.93
8.81
31.15
5.52
q HI •
31
28
13'
10
7
19
16
20
17
5
3
30
31
28
13
10
7
19
16
20
17
5
3
30
31
28
13
10
7
19
16
20
17
5
3
30
1
13
10
7
19
16
17
5
3
ID
FLOW DAY
O.H8
1.44
0.14
0.51
0.05
0.05
0.03
0.10
1.70
1.93
2.63
0.88
1.95
1.44
0.14
0.51
0.05
0.05
0.03
0.10
1.70
1.93
2.63
1.44
4.02
1.50
0.79
0.42
0.05
0.02
0.01
0.03
20
16
20
16
3.11 20
1.76 16
1.27
7.53 2«
9.17
3.30
2.75
0.37
0.13
0.21
20.90
10.99
7 .,93
26
16
Fl_Ci* DAY
FLO*
0.74
0.37
0.74
0.37
0.37
2b.82
17.16
2.27
-------
TRIBUTARY FLO* INFORMATION FO* KENTUCKY
2/3/75
LAKE CODE 2101
LAKE CUMBERLAND
MEAN MONTHLY FLOwS ANU UAILT FLOwS(CMS)
TRISOTAKY MONTH YtArt MEAN FLO* OAY
2I01M1
2101M1
2101P1
210101
3
4
5
6
7
6
9
10
11
12
1
2
3
3
4
5
6
7
8
9
10
11
12
1
2
3
3
4
5
6
7
8
9
10
11
12
1
2
3
3
4
5
6
7
a
9
10
11
12
1
2
3
73
73
73
73
73
73
73
73
73
73
74
74
74
73
73
73
73
73
73
73
73
73
73
74
74
74
73
73
73
73
73
73
73
73
73
73
74
74
74
73
73
73
73
73
73
73
73
73
73
74
74
74
FLO* DAY
FLU* DAY
FLOW
1.30
1.02
1.98
0.74
0.34
0.09
0.01
0.01
1.22
0.99
3.20
0.62
1.13
6.57
5.61
7.73
3.94
1.93
0.37
0.04
0.06
4.42
5.69
16.65
3.74
5.72
26.11
21.52
34.21
19.57
9.23
1.39
0.10
0.13
17.90
21.63
66.26
14.64
22.68
67.54
64.02
65.92
29.93
22.00
6.00
1.05
1.19
49.84
45.87
258.53
41.06
70.79
1
13
10
7
16
20
17
5
16
30
1
13
10
7
19
16
20
5
16
30
1
13
10
7
19
16
17
5
3
30
31
12
17
22
19
22
13
10
8
12
9
9
0.85
1.06
0.54
0.26
0.01
0.00
0.02
2.15
0.25
0.91
4.64
4.25
2.92
1.67
0.15
0.07
0.02
11.16
1.53
4.64
17.87
18.80
14.47
8.04
0.57
0.17
0.34
44.46
29.17
la. 38
65.13
71.64
6V. 94
4.73
2.94
U.45
1.50
4.28
10.70
807.03
37.66
54.37
2B
26
28
26
28
26
16
27
1.76
15.97
9.15
61.45
36.53
6.00
96.28
-------
TRIbOTANY FLOW INFORMATION FOR KENTUCKY
2/3/75
LA
-------
TRIBUTARY FLOW INFORMATION FOH KENTUCKY
a/3/75
LAKE COOE 2101
LAKE CUMBERLAND
MEAN MONTHLY FLO*S AND DAILY FLO*»S(CMS)
TKIBUTARY MONTH YEAtf MEAN FLO* DAY
2101U1
2ioivi
2101ZZ
3
4
5
6
7
8
9
10
11
12
1
2
3
3
4
5
6
7
8
9
10
11
12
1
2
3
3
4
5
6
7
8
9
10
11
12
1
2
3
73
73
73
73
73
73
73
73
73
73
74
74
74
73
73
73
73
73
73
73
73
73
73
74
74
74
73
73
73
73
73
73
73
73
73
73
74
74
74
14.61
6.97
12.97
6.48
3.77
0.65
0.31
0.22
6.40
9.26
22.68
9.66
9.03
5.27
2.46
4.76
2.24
1.30
0.22
0.10
0.08
2.32
3.28
7.84
3.45
3.26
80.42
47.29
70.51
36.53
24.41
6.99
2.32
2.52
48.70
53.24
145.83
48.42
55.22
1
16
22
19
16
14
18
4
1
16
1
13
4
3
30
FLO* DAY
6.54 28
7.39
0.31
0.34
0.31
0.22
0.65
54.65 19
6.57 16
b.4l
2.32 2b
2.86
FLO* DAY
16.a9
FLuw
4.33
6.68
18.89 20
11. 5b
4.53
1.33
-------
APPENDIX D
PHYSICAL and CHEMICAL DATA
-------
iTOK£T RETRIEVAL DATE 7^/01/27
210101
36 51 55.0 085 08 45.0
LAKE CUMBERLAND
21207
DATE
FKUM
TO
73/05/29
73/08/21
73/10/25
TIME DEPTH »
OF
DAr FEET
10
10
10
10
10
10
10
10
10
10
10
10
10
10
10
10
10
10
10
10
10
11
11
11
11
11
11
11
05
05
05
05
05
05
05
05
05
05
35
35
35
35
35
35
35
35
35
35
35
15
15
15
15
15
15
15
0000
0006
0015
0030
0050
0075
0100
0125
0150
0186
0000
0015
0025
0035
0050
0071
0067
0092
0102
0130
0170
0000
0005
0025
0055
0075
0110
0140
00010
TEMP
CENT
17.7
17.4
16. 0
15.1
14.4
13.8
12.5
10.7
9.7
9.4
26.8
26.7
26.0
23.2
20.4
17.1
15.4
14.8
13.1
10.3
9.7
21.5
21.5
21.4
21.2
16.8
12.2
10.7
00300
DO
MG/L
•*.2
8.6
9.0
9.0
9.2
9.6
9.8
9.6
9.2
9.0
9. a
8.6
H.O
5.2
5.8
5.0
2.8
7.0
7.2
6.2
3.6
0.8
0.2
00300
DO
MG/L
•*.2
8.6
9.0
9.0
9.2
9.6
9.8
9.6
9.2
9.0
9. a
8.6
i+.O
5.2
5.8
5.0
2.8
7.0
7.2
6.2
3.6
0.8
0.2
OOU77 00094
TRANSP CNOUCTVY
SECCHI FIELD
INCHES M1CROMHO
72 135
135
125
125
130
130
130
140
145
145
96 136
205
201
198
188
171
157
162
164
167
180
108 130
128
125
125
95
102
116
HEPALtS
3
00400
. PH
Su
7.50
7.50
7.50
7.40
7.40
7.30
7. 40
7.40
7.40
7.40
7.30
6.90
6.60
6.30
6.20
6.00
5.90
5.90
7.60
7.60
7.40
7.00
6.90
b.90
6.90
00410
r ALK
CAC03
MG/L
40
38
37
36
36
36
35
40
42
40
36
34
35
34
28
27
36
49
35
36
36
34
26
38
45
211
0180
00610
•NH3-N
TOTAL
MG/L
0.040
0.030
0.030
0.040
0.040
0.040
0.040
0.040
0.040
0.040
0.050
0.050
0.040
0.040
0.040
0.070
0.060
0.050
0.030
0.030
0.030
0.030
0.030
0.040
0.040
1202
FEET DEPTH
00625
TOT KJEL
N
MG/L
0.400
0.200
0.300
0.200
0.200
0.200K
0.200
0.200K
0.200
0.200
0.400
0.200
0.300
0.200
0.200
0.200
0.200K
0.200K
0.200K
0.200K
0.200K
0.200K
0.200K
0.200K
0.200K
00630
N02S.N03
rt-TOTAL
MG/L
0.300
0.300
0.300
0.300
0.330
0.340
0.350
0.370
0.390
0.390
0.090
0.090
0.1SO
0.380
0.360
0.410
0.450
0.450
0.120
0.110
0.110
0.180
0.370
0.360
0.370
00671
PHOS-OIS
ORTHO
MG/L P
0.006
0.002K
0.005
0.011
0.006
0.006
0.006
0.006
0.006
0.009
0.006
0.012
0.008
0.012
0.009
0.008
0.006
0.008
0.007
0.008
0.009
0.007
0.007
0.013
0.010
K VALUE KNOWN TO BE
LESS THAN INDICATED
-------
STCME.T RETRIEVAL UATE 75/01/27
DATE
FROM
TO
73/05/29
73/08/21
73/10/25
TIME
OF
OAY
10 05
10 05
10 05
10 05
10 05
10 05
10 05
10 05
10 OS
10 05
10 35
10 35
10 35
10 35
10 35
10 35
10 35
10 35
11 15
11 15
11 15
11 15
11 15
11 15
11 15
DEPTH
FEET
0000
0006
0015
0030
0050
0075
0100
0125
0150
0186
0000
0015
0025
0050
0071
0092
0130
0170
0000
0005
0025
0055
0075
0110
0140
00665
PHOS-TOT
MG/L
u.
0.
0.
0.
0.
0.
0.
•J.
0.
0.
0 .
0.
0.
c .
0.
0.
0.
0.
0.
0.
0.
0.
J .
0.
u.
p
015
013
Ul<<
U13
015
01S
018
017
017
018
010
013
012
012
013
039
020
024
008
009
009
010
020
033
043
32217
ChLHPnYL
A
UG/L
1.1
7.5
3.9
2101U1
36 51 55.0 085 Oe <»5.0
LAKE CUMBERLAND
21207 KENTUCKY
llEPALcS
3
2111202
0180 FEET
DEPTH
-------
STORET RETRIEVAL UATE 7t>/01/27
210103
36 52 30.0 085 03 05.0
LAKE CuMdERLAND
21207 KENTUCKY
DATE
FROM
TO
73/05/29
73/08/21
73/10/25
TIME DEPTH
OF
DAY FEET
13 45 0000
13 45 0006
13 45 0015
13 45 0030
13 45 0050
13 45 0075
13 45 0100
13 45 0125
13 45 0145
14 30 0000
14 30 0015
14 30 0025
14 30 0048
14 30 0074
14 30 0100
14 30 0118
10 40 0000
10 40 0005
10 40 0015
10 40 0035
10 40 0055
10 40 0075
10 40 0095
00010
WATER
TEMP
CENT
18.7
18.9
18.3
16.4
13.9
12.4
11.1
10.3
9.9
28.1
27.4
25.5
20.6
16.8
14.1
11.5
21.4
21.4
21.4
21.4
20.6
16.8
14.0
11EPALLS
00300
DO
MG/L
9.0
9.0
8.2
9.4
9.4
9.2
8.6
8.8
9.0
9.0
7.6
4.0
5.2
4.9
6.4
6.8
6.6
1.8
3.0
1.4
00077 00094
TRANSP CNOUCTVY
SECCHI FIELD
INCHES HICROMHO
72 140
140
13S
130
130
150
155
160
170
42 144
139
138
122
112
117
130
120 130
131
130
130
120
110
130
3
00400
PM
su
7. SO
7.60
7.50
7.40
7.40
7.40
7.40
7.40
7.40
7.70
7.50
7.10
6.50
6.30
6.20
6.20
7.30
7.40
7.30
7.30
7.00
6.90
6.90
OOflO
T ALK
CAC03
MG/L
45
45
44
40
39
40
52
54
56
39
36
37
36
32
53
59
38
39
38
39
39
38
53
2111202
0125
00610
NH3-N
TOTAL
MG/L
0.040
0.030
0.030
0.030
0.030
0.040
0.030
0.030
0.030
0.060
0.050
0.040
0.050
0.050
0.040
0.040
0.050
0.030
0.030
0.030
0.030
0.040
0.040
FEET DEPTH
00625
TOT KJEL
N
MG/L
0.400
0.300
0.300
0.300
0.300
0.300
0.300
0.300
0.200
0.600
0.300
0.300
0.200K
0.200K
0.200K
0.200K
0.800
0.200K
0.200K
0.200K
0.200K
0.200K
0.200K
00630
N02«.M03
N-TOTAL
MG/L
0.300
0.300
0.290
0.300
0.320
0.360
0.400
0.420
0.420
0.060
0.060
0.160
0.420
0.400
0.520
0.500
0.120
0.110
0.110
0.110
0.360
0.410
0.440
00671
PnOS-OIS
ORTriO
MG/L P
0.005
0.005
0.007
0.012
0.005
0.005
0.008
0.011
0.008
0.009
0.007
0.006
0.006
0.006
0.008
0.005
0.011
0.008
0.009
0.006
o.ooa
0.010
0.007
K VALUE KNOWN TO BE
LESS THAN INDICATED
-------
STORE! *ET«ItVAL DATE 75/01/27
OATE
FROM
TO
73/05/29
73/08/21
73/1U/25
00t>65 32217
TIME DEPTH PHOS-TOT CHLRPHYL
OF A
DAY FEET
13
13
13
13
13
13
13
13
13
14
14
14
14
14
14
14
10
10
10
10
10
10
10
45
45
<»5
45
45
45
45
45
45
30
30
30
30
30
30
30
40
40
40
40
40
40
40
0000
0006
OJ15
0030
0050
0075
0100
0125
0145
0000
0015
0025
0048
0074
0100
Olid
0000
0005
0015
0035
0055
0075
0095
MG/L P
U.
0,
0,
0,
0,
0.
u,
0
0,
0,
0,
0,
0.
0,
0,
0,
0,
0,
0,
0.
0.
0.
0,
.013
.012
.017
.014
.015
.018
.013
.015
.014
.009
.008
.008
.007
.011
.009
.009
.011
.009
.008
.010
.010
.015
.022
UG/L
1.8
3.U
3.6
210102
36 52 30.0 085 03 05.0
LAKE CUMBERLAND
21207 KENTUCKY
11EPALLS
3
0125 FEET DEPTH
-------
STOKET SETKIEVAL DATE 75/01/27
310103
36 5f 05.0 085 02 05.0
LAKE CUMBERLAND
21207 KENTUCKY
U001U
DATE TIME DEPTH WATER
FROM OF TEMP
TO DAY FEET CENT
73/05/29
If
If
If
If
73/08/21 15
15
15
15
15
15
73/10/25 11
11
11
11
f5 0000
45 0006
f5 0015
f5 0030
45 0050
f5 0075
f5 0097
30 0000
30 0015
30 0030
30 0066
30 0090
30 0100
55 0000
55 0015
55 0035
55 0056
19.5
19.f
19.2
18.
15.
11,
10.
28.
27.8
23.f
17.6
15.2
13.2
21.6
21.5
21.5
20.0
11EPALES
00300
DO
MG/L
8.8
9.0
9.0
9.2
9.6
9.f
8.7
9.1
3.0
f.f
6.0
6.6
6.0
1.2
00077 000*f
TKANSP CNOUCTVY
SECCHI FIELD
INCHES MICROMHO
60 135
130
130
125
125
125
125
70 Ifl
Ifl
136
103
85
89
108 13f
130
130
121
3
OOfOO
PM
SU
7.70
7.70
7.60
7.60
7.60
7.50
7.50
7.70
7.30
6.60
6.fO
6.30
7.20
7.30
6.90
6.90
OOf 10
T ALK
CAC03
MG/L
f7
f7
f6
f3
fl
39
fO
39
37
37
32
35
fO
37
35
3b
2111202
OlOf
00610
NM3-N
TOTAL
MG/L
O.OfO
O.OfO
O.OfO
O.OfO
0.030
0.0*0
O.OfO
0.050
O.OfO
0.050
O.OfO
0.070
O.OfO
O.OfO
0.030
0.030
FEET DEPTH
00625
TOT KJEL
N
MG/L
O.fOO
0.300
0.300
0.300
0.300
0.300
0.300
0.600
0.300
0.200
0.200K
0.300
O.fOO
0.200K
0.200K
0.200K
00630
N02&N03
N-TOTAL
MG/L
0.280
0.290
0.290
0.280
0.300
0.360
0.380
0.070
0.050
0.3fO
0.380
O.fOO
0.130
0.110
0.370
0.380
00671
PiOS-DIS
ORTHO
MG/L P
0.005
0.006
0.007
0.011
0.005
0.006
0.003
0.005
O.OOf
0.011
0.006
0.007
0.006
0.011
0.008
0.010
K VALUE KNOWN TO BE
LESS THAN INDICATED
-------
STOt*ET RETRIEVAL DATE 75/01/37
DATE
FROM
TO
73/05/2S
73/08/21
73/10/25
00665 32217
TIME DEPTH PHOS-TOT CHLRPHYL
OF A
DAY FEET
14
1<»
14
14
14
14
14
15
15
15
15
15
11
11
11
11
45
45
45
45
45
45
45
30
30
30
30
30
55
55
55
55
0000
0006
0015
0030
0050
0075
0097
0000
0015
0030
0066
0100
0000
0015
0035
0056
MO/L P
0.
U,
0,
0,
0,
0.
0,
0,
y,
0,
0,
u,
u,
0,
0,
u,
.015
.014
,015
.014
.018
.026
.022
.008
.008
.013
.010
.029
,017
.012
.015
.016
UG/L
2.4
7.9
2.5
210103
36 5* Ob.O 035 C2 05.0
LAKE CUMBERLAND
21307 KENTUCKY
11EPALES
3
2111202
FEET DEPTH
-------
STOHET RETRIEVAL DATE 75/01/27
210104
36 57 15.0 084 55 45.0
LAKE Cl)M3t«LAND
21207 MiNTUCKY
DATE
FROM
TO
73/05/29
73/08/21
73/10/25
TIME
OF
UAY
13
13
13
13
13
13
13
13
16
16
16
16
16
16
13
13
13
13
13
13
13
50
50
50
50
50
50
50
50
15
15
15
15
15
15
50
50
50
50
50
50
50
DEPTH
FEET
0000
0005
0015
0030
0065
0090
0115
0130
0000
0006
0015
0035
0062
0092
0000
0005
0015
0055
0070
0100
0121
0001U
WATER
TEMP
CENT
19.5
19.5
19.4
18.3
14.5
12.6
11.1
10.5
28.0
28.0
27.5
22.8
18.0
14.7
21.8
21.8
21.5
21.2
17.4
13.2
11.0
HEPALtS
00300
00
MG/L
9.4
9.0
9.2
9.4
9.2
9.4
9.4
8.6
8.6
2.2
2.8
5.2
7.0
7.0
6.0
2.2
0.4
0.4
00077 00094
TftANSP CNOUCTVY
SECCril FIELD
INCHES MICROMHO
36 135
135
135
135
130
130
130
130
60 142
141
140
131
97
89
90 137
127
123
106
100
98
3
00400
PH
SU
7.60
7.60
7.60
7.50
7.50
7.50
7.50
7.40
7.90
7.30
7.30
7.30
7.30
7.30
7.30
7.30
7.00
6.80
6.80
6.70
00410
T ALK
CAC03
MG/L
31
32
32
33
32
33
32
33
40
39
36
36
36
37
34
34
34
35
J9
37
2111202
0097
00610
NH3-N
TOTAL
MG/L
0.040
0.060
0.040
0.040
0.040
0.040
0.040
0.060
0.050
0.040
0.070
0.050
0.070
0.060
0.040
0.040
0.040
0.030
0.040
0.040
FEET DEPTH
00625
TOT KJEL
N
MG/L
0.200K
0.200K
0.200K
0.200K
0.200K
0.200K
0.200K
0.200K
0.400
0.300
0.200K
0.200K
0.200K
0.700
0.200K
0.200K
0.200K
0.200K
0.200K
0.200K
00630
N02«.N03
N-TOTAL
MG/L
0.260
0.310
0.260
0.260
0.290
0.340
0.350
0.420
0.070
0.050
0.340
0.390
0.410
0.120
0.110
0.100
0.150
0.380
0.360
0.390
00671
PnOS-OIS
ORTHO
MG/L P
0.006
0.006
0.007
0.007
0.006
0.007
O.OOb
0.013
0.004
0.005
0.005
0.005
0.007
0.009
0.009
0.009
0.008
0.009
0.007
0.006
K VALUE KNOWN TO BE
LESS THAN INDICATED
-------
STjftET RETRIEVAL OATE 75/01/27
DATt
FROM
TO
73/05/29
73/03/21
73/10/25
00665 32217
TIME UEPfH PHOS-TOT CHLRPHYL
OF A
DAY FEET
13
13
13
13
13
13
13
13
16
16
16
16
16
13
13
13
13
13
13
13
50
50
50
50
50
50
50
50
15
15
15
15
15
50
50
50
50
50
50
50
0000
0005
0015
0030
0065
0090
01 15
0130
0000
0015
0035
0062
0092
0000
0005
0015
0055
0070
0100
0121
MG/L P
0.019
0.022
0.016
0.016
0.017
0.019
0.032
0.024
0.008
0.008
0.022
0.015
0.038
0.013
0.011
0.011
0.020
0.018
0.034
0.039
UG/L
2.3
7.6
1.7
2ioio<,
36 57 15.0 084 55 45.0
LAKE CUMBERLAND
21307 KENTUCKY
11EPALES
3
2111202
0097 FEET
DEPTH
-------
STOSET RETRIEVAL OATt 7S/01/27
210105
36 58 10.0 Oa4 51 30.0
LAKE CUMBERLAND
21231 KENTUCKY
DATE TIME DEPT*
FROM OF
TO OAY FEET
73/05/29 13
13
13
13
13
13
13
73/08/22 10
10
10
10
10
10
10
10
73/10/25 14
14
14
14
14
14
14
14
10 0000
10 0005
10 0015
10 0030
10 0045
10 J060
10 0085
00 0000
00 0015
00 0031
00 0041
00 0055
00 0090
00 0115
00 0132
25 0000
25 0005
25 0015
25 0035
25 0055
25 0070
25 0090
25 0114
00010
HATER
TEMP
CENT
19.8
19.7
16.6
18.5
15.9
13.2
11.9
27.1
27.1
23.6
22.3
19.3
14.7
11.9
10.6
21.b
21.5
21.3
21.2
21.1
17.3
15.0
12.0
11EPALES
00300
DO
MG/L
9.0
9.0
9.0
9.0
9.2
9.0
8.0
7.8
3.4
4.0
3.0
3.0
7.2
6.4
6.4
6.0
0.4
0.1
0.4
00077 00094
TrfANSP CNOUCTVY
SECCHI FIELD
INCHES MICftOMHO
38 140
140
140
140
135
135
135
60 . 143
143
133
126
117
93
93
94
108 139
135
134
132
130
114
114
102
3
00400
PH
SU
7.60
7.60
7.60
7.60
7.50
7.50
7.50
8.10
7.70
6.50
6.90
6.80
6.70
7.30
7.30
7.30
7.30
7.20
6.90
6.90
6.80
00410
T ALK
CAC03
MG/L
40
40
41
32
31
32
33
36
35
32
35
37
39
38
38
38
39
41
46
49
43
211
0136
00610
NH3-N
TOTAL
MG/L
0.050
0.050
0.060
0.060
0.060
0.060
0.040
0.060
0.050
0.060
0.060
0.070
0.060
0.040
0.040
0.040
0.040
0.040
0.040
0.100
0.040
1202
FEET DEPTH
00625
TOT KJEL
N
MG/L
0.500
0.300
0.300
0.300
0.300
0.300
0.200K
0.400
0.300
0.200K
0.200K
0.200K
0.200K
0.300
0.200K
0.200K
0.200K
0.200K
0.200K
0.200
0.200
00630
N02&N03
N-TOTAL
MG/L
0.240
0.240
0.270
0.270
0.320
0.350
0.340
0.050
0.050
0.330
0.430
0.450
0.460
0.120
0.110
0.110
0.120
0.120
0.390
0.260
0.320
00671
PHOS-DIS
ORThO
MG/L P
0.007
0.007
0.003
0.002
0.009
0.008
0.003
0.006
0.005
0.007
0.005
0.005
0.007
0.005
0.006
0.006
0.007
0.008
0.009
0.007
0.009
K VALUE KNOWN TO BE
LESS THAN INDICATED
-------
bT'J*ET RETRIEVAL OATE 75/01/27
DATE
FROM
TO
73/U5/29
73/08/22
73/10/25
00665 32217
TIME DEPTH PHOS-TOT CHLRPHYL
OF A
DAY FEET
13
13
13
13
13
13
13
10
10
10
10
10
10
14
14
14
14
14
14
14
14
10
10
10
10
10
10
10
00
00
00
00
00
00
25
25
25
25
25
25
25
25
0000
0005
0015
0030
0045
0060
0085
0000
0015
0041
0090
0115
0132
0000
0005
0015
0035
0055
0070
0090
0114
MG/L P
0,
0.
0,
0,
0,
0.
u,
• o,
0.
0,
0,
0,
0,
0,
0,
0.
0,
u,
0,
0,
0,
.017
.Old
.018
.020
.Old
.021
.023
.009
.012
.022
.056
.037
.03fJ
.014
.013
.013
.014
.014
,020
.027
.033
UG/L
2.3
8.5
1.7
210105
36 SB 10.0 084 51
LAKE CUMBERLAND
21231 KENTUCKY
30.0
11EPALES
3
2111202
0136 FEET
DEPTH
-------
RETRIEVAL DATE 75/01/27
210106
36 58 45.0 034 42 55.0
LAKE CUMBERLAND
21231 KENTUCKY
DATE
FROM
Tu
73/05/29
73/08/22
73/10/25
00010
TIME DEPTH WATER
OF TEMH
DAY FEET
12
12
12
12
12
12
12
10
10
10
10
10
10
15
15
15
15
15
15
15
15
15
15
15
15
55
55
55
55
55
55
00
00
00
OG
00
0000
0005
0015
0030
0050
0080
0100
0000
0015
0022
0047
0058
0080
0000
0015
0045
0075
0119
CtNT
17.8
17.8
17.7
17.2
16.9
16.2
12.5
27.2
27.2
26.5
20.7
18.3
15. b
21.8
21.5
21.4
16.5
11.8
00300
DO
MG/L
8.4
3.6
8.4
8.2
8.0
8.8
5.8
8.0
2.8
4.3
6.2
6.0
0.1
0.4
00077
TRANSP
SECCHI
INCHES
24
70
84
00094
CNDUCTVY
FIELD
MICROMHO
140
140
130
130
130
130
130
148
148
141
120
109
96
160
156
154
121
110
11EPALES
3
00400
PH
su
7.60
7.60
7.60
7.60
7.60
7.60
7.60
8.80
8.20
6.70
6.90
7.30
7.30
7.30
6.90
6.80
00410
T ALK
CAC03
MG/L
35
36
36
34
35
36
37
43
42
42
39
42
43
39
49
48
211
0083
00610
NH3-N
TOTAL
MG/L
0.060
0.060
0.060
0.060
0.080
0.050
0.050
0.050
0.060
0.060
0.070
0.050
0.040
0.050
0.120
0.230
1202
FEET DEPTH
00625
TOT KJEL
N
MG/L
0.300
0.200
0.200K
0.200K
0.200K
0.200K
0.200
0.300
0.200
0.200
0.200
0.500
0.300
0.200K
0.300
0.400
00630
N02&N03
N-TOTAL
MG/L
0.230
0.230
0.230
0.220
0.220
0.230
0.320
0.060
0.060
0.400
0.440
0.120
0.110
0.120
0.280
0.130
00671
PnOS-DIS
ORTHO
MG/L P
0.010
0.004
0.007
0.006
0.011
0.007
0.011
0.011
0.006
0.005
0.012
0.005
0.012
0.008
0.005
0.010
K VALUE KNOWN TO QE
LESS THAN INDICATED
-------
bTORET
OATE 75/01/27
DATE
FROM
TO
73/05/29
73/08/22
73/10/25
00665 32217
TIME DEPTH PHOS-TOT CHLRPHYL
OF A
UAY FEET
12
12
12
12
12
12
12
10
10
10
10
15
15
15
15
15
15
15
15
15
15
15
15
55
55
55
55
00
00
00
00
00
0000
0005
0015
0030
0050
0080
0100
0000
0015
0047
0080
0000
0015
0045
007t>
0119
MG/L P
li.
0,
0.
0,
0.
0,
C.
0,
0.
0.
0.
0.
0.
u<
0.
0,
.027
.026
.021
.02t
.021
.023
.019
,012
.012
.019
.027
.018
.018
.017
,033
.054
OG/L
1.2
6.4
2.3
210106
36 58 45.0 084 <»2 55.0
LAKE CUMBERLAND
212J1 KC.NTUCK.Y
HEPALtS
3
2111202
0083 FEtT
DEPTrt
-------
STOSET RETRIEVAL DATt 75/01/27
210107
36 59 40.U 084 37 2E.O
LAKE CUMdE«LANO
2119* KENTUCKY
DATE
FROM
TO
73/05/29
73/08/22
73/10/25
TIME
OF
DAY
10
10
10
10
10
10
13
13
13
13
13
13
13
15
15
15
15
15
10
10
10
10
10
10
20
20
20
20
20
20
20
30
30
30
30
30
OEPTri
FEET
0000
0005
0015
0030
0050
0084
0000
0015
0024
0026
0045
0050
0060
0000
0005
0015
0025
0043
00010
WATER
TEMP
CENT
17.6
17.6
17.6
17.4
17.2
15.5
26.9
26.8
25.4
25.7
21.5
19.9
18.0
23.2
22.2
21.8
21.8
21.2
HEP ALES
00300
00
MG/L
8.2
8.2
8.2
8.4
8.4
7.4
6.6
5.0
5.0
6.0
6.5
5.6
5.4
3.2
00077 00094
THANSP CNDUCTVY
SECCHI FIELD
INCHES MICROMHO
4 150
135
130
100
100
100
38 148
148
127
126
121
120
114
60 177
177
170
170
155
3
00400
PH
su
7.60
7.60
7.60
7.60
7.60 ,
7.60
8.20
7.70
6.70
6.90
7.00
7.40
7.40
7.30
7.30
7.10
00410
T ALK
CAC03
MG/L
31
30
31
30
25
26
42
41
27
36
47
44
43
42
42
40
2111202
0064
00610
NH3-N
TOTAL
MG/L
0.110
0.090
0.080
0.140
0.120
0.100
0.050
U.060
0.080
0.080
0.050
0.060
0.050
0.040
0.040
0.070
FEET OEPTri
00625
TOT KJEL
N
MG/L
0.400
0.200
0.300
0.300
0.300
0.200
0.500
0.200K
0.200
0.200K
0.300
0.700
0.200K
0.200K
0.200K
0.200K
00630
N02&N03
N-TOTAL
MG/L
0.240
0.230
0.220
0.240
0.280
0.300
0.100
0.140
0.140
0.340
0.460
0.140
0.130
0.130
0.130
0.130
00671
PrlOS-DIS
OHTrtO
MG/L P
0.025
0.015
0.008
0.005
0.005
0.006
0.006
0.006
0.007
0.022
0.006
0.008
0.008
0.007
0.008
0.007
K VALUE KNOrtN TO 3E
LESS THAN INDICATED
-------
STOHET K£TR1EVAL GATE 75/01/27
DATE
FROM
TO
73/05/29
73/08/22
73/10/25
00665 32217
TIME DEPTH PHOS-TOT CHLRPHYL
OF A
DAY FEET
10
10
10
10
10
10
13
13
13
13
13
15
15
15
15
15
10
10
10
10
10
10
20
20
20
20
20
30
30
30
30
30
0000
0005
0015
0030
0050
0084
0000
0015
0026
0045
0060
0000
0005
0015
0025
0043
MG/L P
0,
0,
0,
0,
0,
0,
0,
0,
0,
0,
0,
0.
0.
0,
0.
0,
.054
.054
.066
.066
,069
.066
.019
.016
,013
.024
.013
.019
.013
.013
.013
,029
UG/L
1.2
3.6
2.4
210107
36 59 *0.0 084 37 25.0
LAKE CUMBERLAND
21199 KtNTUOY
11EPALES
3
2111202
0064 FEET
DEPTH
-------
APPENDIX E
TRIBUTARY and WASTEWATER
TREATMENT PLANT DATA
-------
STO»ET
75/01/13
T !•-'=• HFPT-
FPDM Or
TO OAV FEET
73/04/01
73/04/38
71/06/17
73/07/2?
73/09/1*
73/10/14
7^/01/05
74/01/20
74/02/0?
74/02/17
74/03/17
14 45
06 10
06 '5
10 30
09 10
00 T5
09 IS
13 05
06 30
09 SO
03 00
06 30
2l|pU LS2101A1
36 'p 00.0 C85 08 30.0
CUMBERLAND RIVER
2116s7 7.5 CtfEELSBOSO
0/CUMBEPLANO LAKE
E eitiiJK .d MI 8ELO rtOLF CREEK DAM
llERfiLES 2111204
4 ' 0000 FEET DEPTH
rt"*30
13 <..'•: 03 1
TOT4L
MG/L
0.330
O.?90
0.300
0.320
0.350
0.315
0.3 3 1'
2.300
0.320
0.352
0.360
0.360
C06?5
'^T KJEL
N
*b/L
O.IOOK
6.1*0
0.2SO
0.780
1.450
0.4<*0
0.500
0. 300
0.100
0.200
0.600
u.200
00610
rjri3-N
TjTfiL
•iG/L
C . 0 1 4
0.018
0.030
0.033
0.042
0.0 bfe
O.Cl'3
0.010
0.010
0.020
0.025
O.C?U
00671
Prius-ms
OKTHO
MG/L P
C.005K
0.006
0.0 11
0.005K
0.015
0.005K
U.005K
C.005
0.010
0.010
0.010
0.005
00665
PHOS-TOT
MG/L P "•
0.020
0.020 "
o.o?a
0.020
0.025 *•
0 . 0 ?5 "
0.015
0.035
0.035
0.040
0.065
0.035
K VALUE K'JOWN TO .:.
LtSS THAN IMOiC^TEO
-------
RETVIFV4L PATI 75/01/13
2101A2 LS2101A2
36 50 00.0 084 20 30.0
?POM
TO
73/04/1*.
71/0<*/15
71/05/1'
73/05/13
73/06/17
73/07/30
73/07/31
73/08/18
73/6«/19
73/09/2?
73/09/2J
73/10/30
73/10/31
73/1 1/10
73/11/11
74/n\/l?
74/01/13
74/01/15
74/01/16
OF
•,c nEPf-1 *!0'c:''0~
M-Ti'-T.H.
DAY FtfT MG/L
13
10
13
13
12
13
\?-
1C
13
11
12
10
12
11
13
14
l'»
11
12
13
00
00
no
30
OP
no
"*C
no
00
00
00
00
00
00
CO
00
00
00
00
30
0
II
0
0
0
r\
r,
0
0
0
0
0
0
0
0
0
0
0
0
0
.220
.210
. 19H
.210
.330
.330
.235
.250
.300
.294
.290
. 290
.500
.480
. ?7?
.216
.31?
.268
.288
.28*
21 7.5 CUMBERLAND F
I/CUMBF.fLAtsiD L&KE
rtrfY 90 dROG IN CUMBERLAND FALLS ST PAtfK
IIEPALFS 2111204
•» 0000 FEET DEPTH
T°kjPL
MG/L
0.270
0.260
1.000
0.820
"1.050
1.700
2.90-'
3.^00
3.500
1.3?0
0.420
0.420
0.200
0.^50
0.375
0.400
;*. i DOK
G. 100*.
0. 700
0.900
00610 OC671 00665
K..-M-N PnOS-fMS PHOS-TOT
1" ;7 it ORT.-iO
•-1G/L
0.066
0.048
0.032
0.05P
0.078
0.05?
0.095
0 . 1 6 u
3.120
•J.I 98
li . 1 1 0
0.105
0.032
0.03?
0 . & 6**
o.u 32
u . 0 4 0
0.0<+Q
0.050
0.045
MG/L P
0.007
0.006
0.007
0.026
0.008
0.009
0.005*
U.020
0.017
0.015
J.U37
0.042
0.02*
0.0 2<*
0.028
0.016
0.020
0.010
0.010
0.010
MG/L P -
0.055
0.030
0.200
0 . 1 95.
0.110
0.100
U.035
0.037
0.092
0.065
0.105
0.100
0.045
0.065
0.050
0.040
0.020
0.020
0.020
0.025
K VALUE KNOrfN TO B£
LESS THAN INDICATED
-------
OflTE 75/CM/13
TIMP DFOT
OF
TO 04Y FEET
73/03/31
73/06/17
73/07/2?
73/08/10
73/10/1^*
73/11/H
74/01/05
74/01/20
74/02/0?
74/02/17
74/03/17
12 30
oe 45
03 OS
10 00
08 45
09 00
0* 40
09 00
15 10
08 45
10 00
14 15
09 55
2101B1 LS210181
36 tff, 30.0 085 OC 00.0
21 7.b «OLF
T/CUMBESLAND LAKE
dROG (ST HWY 1266) NEAK SEVENTY SIX FALL
11EPALES 2111204
4 0000 FEET OEPTrt
f ." *• 3 C
N0~ •."03
x.i-T ITiL
M'j/L
C.91S
0.740
1.440
1.440
1.100
'1.700
0.560
O.SbC
1.230
1.010
0.7HO
1.040
0.870
00625
TOT KJEL
r<
MG/L
0.2^0
0.3SO
0.720
0.330
1.900
O.?e?0 .
0.8 On
0.600
0.400
0.400
1.200
1.000
1.000
C'.'fclO
V-, "5-,u
TOT AL
MG/L
'1 . U 1 S
0.052
0 . C 37
0.031
0.046
.0.037
0.036
0.023
0.010
0.025
0.115
0.080
0.075
00671
Pnrs-015
lVTri(j
MG/L P
0.007
0.013
0.00ft
0.007
0.010
0.007
u.ooa
y . o 1 2
0.010
0.015
e.006
0.010
0.010
00665
PHOS-TOT
MG/L P
0.020
0.035
0.040
0.015
0.0?0
0.015
0.015
0.030
0.030
0.020
0.028
0.030
0.030
-------
STOPFT -£T
OATE
OATE
TO
73/03/31
73/Oft/l"'
73/07/22
73/08/19
73/01/1^
73/10/14
73/10/20
73/11/13
74/01/05
74/01/20
74/0?/02
74/02/17
74/03/17
OF
OAT F
14 55
08 30
09 30
08 45
OS ?0
0« 40
OB 30
14 00
03 30
14 45
08 15
09 30
14 00
08 30
LS2101C1
36 46 30.0 085 06 30.0
21 •: 7.5 CUMBERLAND C
T/CU«bE^LAMD LAKE
iT RD 55* BivDG 1.5 MI U OF ARLOW
llEPALtS 2111204
4 0000 FEET DEPTH
On^3')
j3»VO? i
-TOTAL
MG/L
J . 700
0.690
9 . <> 30
O.«70
0.600
0 . ' o ?
r. 3 "7 ;}
C . c " .)
0 . 5 0 *>
1.5P3
1 . 1 n 0
0.756
1 . 1 rt 0
O.P.-iO
r n52^
ror KJFL
M
•«G/L
0.220
0.100K
1.050
0.780
1.530
0. 3*0
0.COJ
l.«50
0.300
(.> . 1 •.) 0
0.600
0.600
1 .700
0.7QO
o 0^10
>.~3-N
i .HAL
•iG/L
u.040
0.034
U.Ola
0.024
0.050
0 . 0 3 H
0 . 0 1 9
0.052
0.020
0.010
0.025
0.042
o.090
0.045
00671
PHCS-HIS
OPTHQ
MG/L P
G.005K
0.005K
U.007
0.005K
0.007
O.OOSK
O.OOH
0.028
0.005*
0.010
0.005
0.010
0.010
C.005K
00665
PHOS-TOT
MG/L P .
0.005*
o.o ri
0.015
0.010'
0.020-'
0.020
0.020
0.055
0.030
0.025
O.OOSK
0.050
O.U05K
K VALUE KNOWN TO at.
LESS TH^N INDICATEO
-------
STOPET
-ATE ^
21fli|Dl LS2101D1
36 V$ 30.0 084 5.9 00.0
OTTEW CP.EEK
21 ', 7.5 PASNELL
T/CUMBE3L4NO LAKE
5T HtfY 90 3«DG 0.5 MI N OF ZULU
11EPALES 2111204
4 0000 FEET DEPTH
D«TF
FPON'
TO
73/04/01
73/C4/29
73/06/17
73/07/22
73/OP/19
73/C9/l<-
73/10/1"
73/1 1/19
7^/01/05
74/01/20
7^/02/0?
74/02/17
74/03/17
TI'-
Or
00630
»E OF^fn NO'*. NO 3 "
N-TOTAL
OAY FEET
13
09
10
11
10
'.0
10
09
12
09
09
10
09
15
20
00
05
00
^0
20
30
<*Q
10
30
20
20
MG/L
0
!.'
0
0
0
5
0
0
0
0
0
0
0
.32J
.270
.240
.126
.100
.100
.lt>4
.460
.6t>0
.530
.616
.420
.340
00625
roT KJFL
N
MG/L
0.
0.
0.
0.
1.
1.
- 0.
0 .
0.
0.
0.
0.
1.
140
10C"<
930
540
200
050
450
•400
100
300
500
800
500
00610
Nji-O-N P
Ti;TftL
MG/L
C.
0.
0.
0.
0.
V •
0 .
0.
0.
u.
0.
u.
0.
050
006
015
015
013
0'4?
02S
012
005K
020
015
065
125
C0671 00665
•HOS-OIS PHOS-TOT
OPTrlO
MG/L
0.
0.
0.
0.
0.
0.
0 .
0.
0.
0.
0.
0.
0.
P
005K
005K
005K
005K
006
005K
005K
OOSK
005
005K
015
005K
005K
MG/L P
0.010
0.015
0.015
0.020..
0.040J;
0.010
0.010
0.015
0.009
0,0 05K'
0.010
0.005K
K VALUE KNOWN TO 8t
LESS THAN INDICATED
-------
STO»tT ^ETRIEvSL
75/01/13
21&E1 LS2101E1
36 49 02.0 084 53 00.0
21 - 7.5 PMNELL
T/CUMBERLANO LAKE
sr HWY BWOG 2 MI w OF MONTICELLO
11EPALES 2111204
4 0000 FEET DEPTH
00630 00625
OATT TIMF DEPTH NO??.N03 TOT KJEL
fPOw OF N-TOTAL N
TO
73/04/01
73/04/28
73/06/17
73/07/22
73/OS/19
73/09/16
73/10/U
73/11/13
74/01/04
74/01/19
74/02/01
74/02/1*5
74/03/16
DAY FEET
12
14
10
12
11
1 6
12
11
16
12
14
11
11
45
45
00
30
05
?5
00
30
00
00
00
20
00
MG/L
1
0
0
1
2
2
?
0
I
2
1
1
1
.020
.610
.080
.620
.400
.200
.000
.020
.260
.100
,84C
.520
.700
"1G/L
0.
0.
1.
c.
6'.
c.
0.
0.
0.
0.
1.
0.
0.
460
620
035
100K
200
400
650
150
200
100K
300
425
500
00610 30671 00665
•:-4-i3-M PHOS-OI5 PHOS-TOT
TOTAL OPTrtO
MG/L
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
115
176
065
013
005K
032
010
012
015
025
055
055
052
MG/L
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
p
030
066
008
176
400
610
650
005K
035
080
060
090
090
MG/L P;«-
0.050.
0 . 1 15?:
0.050
0.190
0 . 4 5(K
0.650
u.700
0.025
0.085
C.090'
0.075:"
0.115
0.130
K VALUE KNOWN TO BE
LESS THAN INDICATED
-------
STOPET 5£7«IEV4L' OATE 7S/C1/13
0*TF TTVF
TO
DAY FFET
73/04/01
73/04/28
73/05/13
73/06/10
73/07/07
73/0-V19
73/09/1^
73/11/17
74/01/05
74/01/20
74/02/03
74/02/16
74/03/30
11
10
10
12
!0
I?.
11
11
10
15
15
11
12
10
00
30
00
30
00
30
"S
3C
30
00
00
00
LS3101F1
36 56 00.0 084 46 00.0
21 7.5 MILL SPRINGS
T /CUMBERLAND LAKE
PPIV.ATE 3RDG .5 MI M OF MILL SPRINGS
11EPALES 2111304
^ 0000 FEET DEPTH
03630
NO 2s* MO 3
N-T"TAL
MG/L
0.63C
0.336
0.690
1.020
0.160
0.750
0.330
1.040
0.924
0.710
0.5?R
0.850
0.430
00625
TOT KJFL
N
*G/L
0.190
0.335
0.200
0.540
1 ,890
2.400
0.860
0.237
0.400
. 0.700
0.300
0.100
0.700
00610
NH3-N
TOTAL
MG/L
0.035
0.033
0.015
0.105
0.044
0.084
0.069
0.008
0.110
0.085
0.015
0.005K
0.027
00671
PHOS-DIS
ORTHO
MG/L P
0.006
0.016
0.007
'0.015
0.009
0.0?4
0.017
0.024
0.020
0.030
0.020
0.012
0.009
00665
PHOS-TOT '
MG/L J
0.025 ';
0.040^
0.035 .
0.035 :
0.040 ft
0.030
0.045
0.030
0.045
0.060 ~
0.045 '
0.020
0.070
K VALUE KNOWN TO BE
LESS THAN INDICATED
-------
STO°ET RETRIEVAL OATr 75/31/13
TO
TIVE DE'-'TM
OF
OAY
73/03/31
73/04/2^
73/05/13
73/06/10
73/07/07
73/01/1"
73/09/16
73/10/20
73/11/17
74/01/05
74/01/20
74/02/03
74/02/16
74/03/30
10
09
10
10
10
10
\?
10
12
10
14
14
14
11
20
30
30
00
30
30
30
1-5
45
00
00
CO
00
30
ZltlGl LS2101G1
36 59 30.0 085 02 30.0
21 . 7.5 JAMESTOWN
T/CMHBE«L«ND LAKE
BANK 100 Y3DS S HKY 619 0.5E JAMESTOWN
11E£»LE5 2111204
4 0000 FEET DEPTH
0630
'JA'03
OT4L
G/L
0.5«D
0.470
0.66C
0.680
C.6SO
O.SOO
0.590
0.910
0.336
1.300
0.7Q2
O.HIO
0.730
?.710
00625
TOT KJEL
\
MG/L
O.P50
0.380
0.720
0.280
1.150
2.700
3.600
0.900
0.150
0.200
0.200
0.250
0.300
0.900
00610
,^H j-N.
TOTAL
MG/L
0.023
o.oa<*
0.138
0.026
0.031
0.07S
0.3S9
0.096
0.012
0.025
0.025
0.020
0.020
0.0^0
00671
PH05-OIS
ORThO
MG/L P
0.115
0.066
0.060
0.270
0.140
0.510
0.440
0.580
0.012
0.015
0.110
0.110
0.260
0.005
00665
PhOS-TOT
MG/L P '
0 . 1 35
0.110
0.120
0 . 300
0 . 1 70 :
0.550
0.490
0.650
0.015
0.025
0.155
0.145
0.315
0.030
-------
STOPFT
21$}H1 LS2101H1
37 02 30.0 084 53 00.0
H09SC CSEEK
31 7.5 f-LI
T/CUM8E»LANO LAKE
ri-?OG ON LIGHT DUTY RO 1 MI E DORENA
11EPALES 2111204
4 * 0000 FEET DEPTH
OaTF TIME n€=Tr
FPO^ Of
TO
73/03/31
73/04/2°
73/06/10
73/07/07
73/03/19
73/09/ 1 f"
73/10/20
73/11/17
74/01/05
74/01/20
74/02/03
74/0'V i*,
74/03/30
L.AY Fter
12
10
! 1
11
11
i "*.
1?
12
11
15
15
13
13
3C
10
00
30
30
in
00
45
00
15
30
00
00
' 0 "
.x-Tf:
^30 I-062S
Ki03 TOT KJtL
TAL N
MG/L
C
0
0
C
0
0
0
0
1
0
0
0
0
.530
,4'"»C
.910
.920
.220
.110
.0'.-;
.7*0
.300
.810
.850
.67?
.710
00610 00671 0066S
.\c-n-N PHOS-OIS PH05-TOT
>IG/L r-*b/L
0.
0.
0.
0.
3.
1.
0.
0.
0 .
0.
0.
(i *
0.
2^0
200
130
340
600
"00
300
150
100K
200
100K
100K
400
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
017
017
016
022
110
13?
016
OOP
005
010
015
nio
015
MG/L
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
p
008
Oil
012
021
022
007
028
005
010
020
015
010
010
MG/L P
O.U15 "
0.020 *
0.020
0.025
0.0 3
-------
21XWJ1 LS2101J1
37 02 30.0 084 53 00.0
21 7.5 F.LI
T/OJKBE^LANO LAKE
TrfAU. .25 MI OFF DIRT RO 2 MI E DORENA
IIEP'ALES 2111204
4 0000 FEET DEPTH
TtTF
FROM
TO
73/03/31
73/04/2S
73/05/13
73/06/10
73/07/07
73/08/1Q
73/0'Vl'S
73/10/20
73/11/17
74/01/05
74/01/20
74/02/03
74/02/16
74/01/30
Ot.":>3G 00625
HMC nf-.oT.-, MuovjCn TOT KJEL
OF :*J- TOTAL N
Oav FEtT MG-'L MG/L
12
10
12
10
1?
1.?
13
12
13
11
15
15
1?
13
'0
15
IS
&5
00
?0
45
30
30
30
30
?0
00
•^5
0
0
0
0
0
0
,•»
j\
0
1
0
c
0
p
.660
. .
0.
0.
0.
0.
0.
0.
0.
c.
0.
0.
0.
0.
0.
c.
OOSK
13fl
014
016
042
020
720
360
012
010
010
005
010
040
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
007
007
005K
005K
00<»
010
006
020
016
010
015
010
005
005
-- -i-"
0.010
o.o^r
0.010
0.010-
0.0 2S-;
0.015
0.025
0.045
0.016
0.025
0.015
0.010
0.040
K VALUE KNOWN TO BE
LESS THAN INDICATED
-------
LS2101K1
36 £? 30.0 085 45 00.0
v*Hlffc oaK MEEK
21~ 7.5 MILL SHSINGS
T/CUMBE3L4NO LAKE
END,RD OFF HWY 235 0.5 MI WOF TRIMBLE
11EPALES 2111204
4 0000 FEET DEPTH
CDQM
TO
73/03/31
73/04/28
73/05/13
73/06/10
73/07/Q7
73/Q8/H
73/09/ j •-,
73/10/20
73/11/17
74/01/05
74/01/20
74/02/03
74/02/1*
7&/03/30
T'VF O'.-T-
OF
00
•i NO"'*
DAY FEET wo
09
13
11
13
11
13
12
15
13
15
14
16
17
11
It
30
6=;
00
15
65
00
45
00
30
00
3C
?C
00
00
45
0
0
J;
0
1
1
o
0
0
0
1
1
1
0
n
630 JC625
MO 3 TOT xj~l.
TflL N
/L
.2?:
.830
.720
.920
.020
.100
.110
.169
.020
.840
.30U
.180
.200
«°f>v
.710
OUclO
TOVflL
iG/L . -lu/L
0.
5.
0.
0.
0.
0.
0.
I.
0.
0.
0.
0.
0 .
0.
1.
130
1QC
45;
130
? Q
!3 -I t J
320
30 0
100K
300
100K
100K
100
ooc
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
c .
0.
0 .
•:, .
0 .
040
006
130
016
015
032
01<-
168
036
00^
035
005K
010
005
0*5
00671 00665 "
viOS-OIS PHQS-TOT
cm-io
MO./L
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
p
005K
008
008
008
OOR
Oil
OOB
013
016
016
015
015
020
005
005
Mu/L P '.
o.oisV
0.0 IS"
0.020,
o.oi$":
d . 0 15"
0.025
0.020
0.025
0.055
0.016
0.025
0.015
0.020
0.005"
0.035
K VALUE KNOWN TO BE
LESS THAN INDICATED
-------
75/01/13
OATF. HMF r>cc>T-i
rpoM OF
TO DAY FEET
73/04/01
73/04/29.
73/"5/13
73/06/10
73/07/07
73/-)ft/19
73/0^/16
73/11/17
74/01/05
74/01/2*-
74/02/03
74/02/16
74/03/30
11
10
09
12
10
13
IS
14
10
10
11
15
30
45
00
30
on
?:)
10
on
30
00
N-TOfiL
MG/L
j . 4 3 0
O.MO
1.340
0 .Ode
0.0^0
•J . 0 1 7
3.9 J j
0.7-92
0.6 30
0.67?
0.630
C.blO
00625
N
MG/L
0.25\.'
0.340
0. 660
0.480
O.?90
1 . 37P
1.700
0.15C
&.200
0.200
0.400
0.300
0.300
2101LI LS2101L1
37 06 00.0 084 41 30.0
FISHING C3EEK ASM
21 7.5 DcLMAS
T/CUM3£-?LANO LAKE
ttRDG CUMBERLAND PARKWAY 3 MI * SOMERSET
11EPALES 2111204
4 0000 FEET DEPTH
~* 0 6 1 3
'••-I3-M
:-ib/L
0.0 1C
O.C7Q
0.1 7(j
0.058
O.OO-:)
0.005K
0.540
0 . 0 1 0
0.010
0.010
0.050
0.005
0.020
00671
PnOS-niS
MG/L P
O.DOSK
0.006
O.OOSK
0.005K
0.037
0.005K
0.015
0.015
0.010
0.010
0.005
00665
PHQS-TOT
MG/L P
0.020"
0.015
o.oid;-
0.015-
0.040
0.040
0.040
0.050
0.045
0.035
0.030
K VALUE KNOWN TO HE
LESS THAN INQIC^TEU
-------
2101M1 LS2101M1
37 02 30.0 084 36 00.0
SINKING C^EEK
21 7.5 SOMERSET
T/C>JM6EWL4iND LAKE
IOC FT oELO CULVERT ON LGT DUTY ROAD
11E°6LES 2111204
4 oooo FEET OEPTH
09 41
... 09 45
73/fJVH 10 30
73/0^/10 09 30
73/OV07
73/OV/is 13 00
73/IVpr, )S ,0
73/11/ir 10 30
74/0 I/OS 09 30
74/0?/|«, 09
09
•f: ": 6 3 ..-
••iO?sfl03
N-T3T.1.L
Mr, /i_
i.aco
1.44G
1.S4C
?.700
0.090
?.06G
3.504
4.1v,3
1 . «50
1.500
?.ooo
1 .600
•'O'v?^
TOT KJEL
w
•if-/L
0.260
0.5PO
0.580
0.670
?.730
4. 400
•J.*'5
0.1 OOK
0.300
1.100
1.100
1.000
0^610
^M3-^
T-)TiL
M-'i/L
0.069
0.1 6C
0.170
0.357
0.072
?.?00
0.036
0.02?
0.060
0.140
0.390
0.170
00*71
Pbos-ors
0&T-HO
HG/L P
0.250
0.210
0.290
0.650
0.005K
0.040
0.130
0.250
0.890
0.310
00665
PHOS-TOT
MG/L f
0.290
0.310
0.390
0.700
0.015
0.042
0.185
0.450
0.970
0.4tO
K VALUE KNOWN TO Be
LESS THAN INDICATED
-------
75/GI'i?
21«1N1 LS2101N1
37 02 30.0 064 35 30.0
PITMftN C-?L£K
?.\ 7.S SOMERSET
T/CUMb£*LA.MO LA«E
ST RO 1247 S^OG 2.5 MI S OFSOMERSET
211120*
0000 FEET DEPTH
TO
DAY Ft£T
73/34/01 09 ?5
73/04/?3 09 50
73/05/n 10 45
73/06/10 09 45
73/07/07 00 45
73/08/13 11 ?5
73/09/1^ 14 00
74/01/05 11 45
09 50
74/03/30 09 30
Ti'63'v,-
r;f, ->:. MQ-)
!s!-TOTfc,_
MO/L
U.7*0
0.710
0.980
0.910
1.1 fcU
o.66c
o.oio<
1 . 3 J 0
1.P10
0.870
O.»00
OCft'S
T-n KJ£L
^J
MG/L
0.100K .
0.630
0.56C
0.2J-0
0.1?0
2.30C
i . i o :
.0.100
C.500
0.100
0.600
o : M o
,Vr->;j-M
T-'-TflL
MG/L
0.007
0.164
0.1*9
0.054
0.011
0.034
0.076
0.010
0.025
G.C-30
0.035
00671
PHOS-OIS
ORTHO
MG/L P
O.Oub
0.027
0.032
0.030
0.007
0.005K
0.005K
0.015
0.045
0.030
0.055
OC665
PHOS-TOT
MG/L P
0.020
0.060''"
0.050
0.032
0.025
0.025
0.035
0.033
0.080.
0.045"
0.095
K VALUE KNOWN TO B£
LESS THAN
-------
7S/&1/13
TI'4F Dt°T-' -iO'>v
TO OAV FEET
73/04/01 1C ?C
73/04/28 09 10
73/05/13 15 00
73/06/10 10 30
73/07/07 11 ?0
73/OB/l=> 1? 10
73/09/16 13 30
74/01/05 09 «5
74/02/03
74/02/16 09 00
74/03/30 10 20
1 v f '-J 0 3
. , T • |
•r,',L-
0.510
0.330
0.530
0.04?
0.044
0.050
0 . 0 10 \
0.7'S
0.640
0.660
0.640
0.4 SO
cjT *J~L
MC-/L
0.170
0.270
0.420
0.490
0.460
3.10'J
1 .760
0.1 OU
1.000
0.100
0.250
0.400
OOclO
TOT4L
MG/L
0.007
0.048
0.063
0.033
O.OOfl
0 .102
0.010
0.035
C.035
0.012
C.C15
OPT HO
MG/L P
0.006
O.OOB
0.020
0.005K
O.OOSK
0.005K
0.005*
0.020
0.012
0.010
0.005
C.007
210JP1 LS2101P1
36 5S 30.0 034 29 30.0
HUCX C^EE*
21 t,r> HAIu
3Y 30AT DOC 1.1 S NORTHFIELOON RO 769
HtPftLf.S 2111204
4 0000 FEET DEPTH
00665
MG/L P
0.025
0.020:
0.045
0.040
0.025
0.040
0.045
0.040
0.017
0.020
0.010
0.060
K VALUE KNOWN TO -it
LESS THAN INDICATED
-------
STOPET
210101 LS210101
37 01 30.0 08<* 19 30.0
H'OCKCASTLf.
?1 7.
n,
-------
STO&ET
c 7S/01/13
TO
73/03/31
73/05/1?
73/06/17
73/07/2?
FEET
10
n
13
16
II
10
40
00
50
10
00
73/09/2? 13
73/10/13 12 50
73/11/10 14 10
73/42/^|«~ 12 05—
74/01/1? 1? 00
74/01/27 15 10
74/02/0-5 11 00
74/03/00 12 30
*!' LS2101«1
36 SH 30.0 U84 16 30.0
LAUREL WIVE1*
21 7.5 SiV»YtK Kf
T/CUM8EKLauO LAKE
tMD BAL!>OCK-LAUKEL SO 2 MIS BALO«OCK
2111204
0000 FEET DEPTH
f ..-30
N0"i,'.0 i
N-TOTiL
MG/L
0.320
0.315
C.5?d
0.140
0 . '0 0
0.1 -»7
-j .056
0 . ? « f!
— <)-. 36ft
0.352
0.352
0.343
0.320
30625
T:.T KJFL
XJ
MG/L
0.440
0.460
0.730
3.150
0.630
2.300
- — ;&»>]B«0s:
0.900
4.000
0.500
0.775
o -"-.10
\-T<-M
TOTAL
M-?/L
C.105
0.046
i). 089
0.058
0.027
0.520
1.120
0.540
—v- ft»ft6*-
~" ~ 0.075
0.200
0.040
0.050
00671
?HQS-')IS
OPTnO
MG/L P
0.015
0.0 29
0.023
0.029
0.019
0.019
G.024
0.020
- - 0.020
0.010
0.015
0.015
0.010
C.TS65
DnOS-TOT
MG/L P
0.060
0.115
0.110
0.055
0.030
0.065
0.060
0.040
• 0^075'
0.030
0.025
0.025
0.050
-------
STORE! RETRIEVAL DATE 75/01/?0
2101S1 LS2101S1
36 55 00.0 034 25 30.0
BEAVER C«EE;K
21 7.5 H«IL
T/CUMBE^LAND LAKE
BOWMAN RO B30G 2 "I NW OF FUNSTOWN KY
11EP/VLES 2111204
4 0000 FEET DEPTH
DATE TIME DEPTH
FROM OF
TO DAY FEET
73/04/01
73/04/28
73/05/13
73/06/10
73/07/07
73/08/19
73/09/22
73/10/20
73/11/17
74/01/05
74/01/27
74/02/03
74/02/16
74/03/30
09 45
09 30
09 30
09 30
09 15
11 00
10 30
12 00
11 00
10 00
13 45
14 00
09 45
11 00
i0630
'&N03
OTAL
IG/L
0.027
0.012
0.042
0.240
0.044
0.050
0.05?
0.016
0.072
0.064
0.060
0.064
0.184
0.080
00625
TOT KJEL
N
MG/L
0.100K
0.130
0.100K
0.150
1.600
3.800
0.210
0.100K
0.100K
0.100K
0.100K
0.100K
0.200
0.700
00610
NH3-N
TOTAL
MG/L
0.015
0.025
0.044
0.025
0.040
0.037
0.044
0.020
0.008
0.020
0.020
0.030
0.065
0.045
00671
PriOS-OIS
ORTHO
MG/L P
0.005K
0.005K
0.005K
0.012
0.005K
0.005K
0.005K
0.010
0.008
0.005
0.005
0.005K
0.010
0.015
00665 50051
PHOS-TOT FLOW
RATE
MG/L P 1NST MOD
0.010
0.010
0.005K
0.015
0.005K -
0.010
0.005K
0.010
O.OOH •*•
0.005
0.005
0.005K
0.010
0.020
50053
CONOU I T
FLOW-MGO
MONTHLY
K VALUE KNOWN TO 8E
LESS THAN INDICATED
-------
21001 LS2101T1
36 41 30.0 OB4 32 30.0
S FOtfk CUMBERLAND
21 7.5 RARTELL
92 83JG 3 Ml
11EPJSLES
4 .
OF SMITHTOWN
2111204
0000 FEET DEPTH
04TF
fPOM
TO
73/6^/01
73/04/2«
73/06/1*
73/07/22
73/C8/19
73/6=5/1"
73/TO/K
74/0 1/04
T4/O1/19
74/02/01
74/02/16
74/03/15
00630 00625 C:'"
TI'-'F Oc°T-i NiO'-N';03 TOT KJtL IM-V.J-
of SI-TOTAL n ror.
-.10 ?0671
PI-.OS-OIS
iL 0»THO
D4Y FtET MG/L MG/L -'G/L
0 9
I?
13
10
10
rm
11
00
11
13
10
10
45
10
30
00
00
30
00
">5
30 — -,
15
30
00
0.138
0.132
0.130
0.025
0.100
0.075
O.C63
0.20i?
.,,.0*240 — -
0.200
0.165
C.I ^4
0.260
1.100
0.400
0.220
6.180
0.27C
1.000
0.500
0.100K
6.100
0.600 '
0.400
0.
0 <
0 ,
0.
0.
0,
-\
'1 1
•'),
0.
c,
ft
i' <
.02I1-
.147
.01^
.031
.017
.063
,f 4u
.03u
,020
.02^
.050 "
.04(1 .
MG/L ?
G
0
0
0
0
0
C
0
.005K
.007
.005*
.005K
.005K
.005K
.009
.010
00665
•JHOS-TOT
MG/L P
0
0
0
0
0
0
0
.045
.045
.010
.020
.015
.010
.115
4
•\
j
-'.
*..
•r
*¥
'-•
0»005H; - -OvOOSKji
0
0
0
.005
.005
.005K
0
0
0
.020
.010
.030
^-^
K VALUE KNOWN TO dE
LESS THAN INDICATED
-------
"AT" 7~/
2101U1 LS2101U1
36 4JB 00.0 084 36 00.0
LITTLE S FO-K CUMBERLAND
21 7.5 NEVELSVILLE
T/CUMBERL-i'MO LiKE
f KtEOOM C-IU*CH RO BROGE
IIEP'ALES 2111204
4 0000
OEPTri
DATE .
FROM
TO
73/04/01
73/Oi/?e*
73/06/16
73/07/22
73/06/19
73/09/16
73/10/1"
73/11/1°
74/01/04
74/01/19
74/6?'01
74/6?/16
74/03/16
OF
DAY FEET
11
13
14
09
0>?
04
0Q
09
15
10
16
09
09
15
55
50
30
30
?0
45
30
03
30
00
OS
15
00*30 C0625
i NO'f.M03 TOT KJFL
N-TOTAL N
MG/L
0
0
0
0
0
n
0
0
0
0
0
0
.110
.110
. 1*0
.200
.0^0
.24;)
,0?4
.?76
.??4
.13-*
.166
.092
MG/L
0.
0.
0.
0.
3.
n.
C.
0.
0.
Q.
0.
0.
0.
200
350
560
330
600
50 C
6r>0
450
300
100K
100
40?
200
'M-10
1 JT=>L
•..IA/L
0.
0.
0 .
0.
0.
>"> .
0.
0.
0.
0.
C.
0.
0.
032
070
CO*
016
030
flA-
017
CuP
005
030
005
0?5
015
'D0671
JHOb-nib J
OPT-iO
MG/L P
\}
0
0
0
0
0
0
0
0
0
0
0
.005*
.007
.007
.005K
.005K
.005K
.006
.008
.010
.005
.005
.'005K
00665
rlOS-TGT
WG/L P ,
0.015 '
0.030 *
0.015 .
0.015 ];.
0.010 -•
O.U35 '
0.015
0.040
0.030j£.
0.005^
0.005K
0.020
0.005 -,.
K VALUE KNOWN TO dt
LESS THAN INDICATED
-------
STOSET 3FTPirvi._ OSTc: 75/1.1/i 3
2101V1 LS2101V1
36 52 30.0 064 37 00.0
SI:-;*IMG CJE£K
?1 7.5 NEVELSVILLE
T/C'.IM6E3LA\'0 LAKE
KOCKY HILL 3D ^KOG .25 MI EZION CHURCH
llfl^ALES 2111304
4 0000 FEET DEPTH
01TE TI'F HE.-5!-
FPOM 0*-"
TO o-r FEET
73/04/0} I? 45
73/04/29 1C &5
73/05/13 K ^0
74/01/04 11 40
74/01/20 12 45
74/03/30 1? 45
'••:!-
|0?S1'.1
N-f'M
•1G/
1.
0.
'.; .
r,
0.
•J •
').
T,
O'J
^ I
L
1*30
1 10
094
216
?%%
17'.
Q P.J
006? 5
T )T KJEL
N
•-IO/L
C.130
0.200
0.150
0.600
0.700
0. 1C Of.
t .30o
-.- 'jrlv
" i3-'-
TOTAL
M'J/L
C . C 1 1
0.105
0.04^
0.145
0.030
:'• . 0 1 C
C . 0 1 ^
OO"??!
^-iOS-DJS
O^T-iO
HG/L P
C.OC5K
0.007
0 .006
0.005
0.005
O.OOS
0.015
OObto
3HOS-TOT
MG/L r>
0.022
0.025
0.015
0.015
0.010
0.020
0.025
K VALI.lt rt'
LESS THIN
TO BE
-------
5TORET RETRIEVAL DATE 7f>/0?/G3
2101AA T1-2101AA
36 44 30.0 08* 09 30.0
P003687
LAKE
DATE
FROM
TO
73/04/13
73/06/12
73/07/09
73/08/10
73/09/11
73/10/10
73/11/10
73/12/10
74/01/10
74/02/15
74/03/10
74/04/15
TIME 1
OF
DAY
14
14
10
1*
14
10
10
10
14
09
I
00
30
00
00
00
00
00
00
00
30
FEET
CUMbtRLANU K IV
iltPALES
00630
N02NN03
N- TOTAL
MG/L
0.260
O.<»10
0.525
0.370
3.000
0.560
0.500
0.500
0.680
0.440
0.040
0.262
00625
TOT KJEL
N
MG/L
0.310
1.400
1.400
7.600
5.800
0.400
O.bOOrv
0.500K
0.500K
l.OOOK
1.200
l.uOOrt
OJ610
Nhj-N
TOTAL
MO/L
0.139
0.365
1.060
1.320
0.183
0.290
0.260
0.170
0.097
0.110
O.CSOK
0.010
OU671
PnOS-JIS
urtlrlO
MG/L H
0.129
U.180
0.585
0.840
3.020
O.SOu
0.620
0.0b4
0.170
0.073
0.050K
0.610
4
OU665
FhOb-TOT
Mb/L P
0.182
0.410
0.795
1.470
3.250
0.525
O.blO
0.100
0.310
1.050
0.610
50051
FLOw
RiTt
INST MliD
0.206
0.288
0.336
0.270
0.296
0.184
0.228
0.145
0.243
0.225
0.395
0.250
Erf
2141204
0000 FEET
50053
CONDUIT
FLOX-mii)
MONTHLY
0.250
0.225
0.302
0.225
0.250
0.190
0.218
0.208
0.264
0.266
0.199
0.330
OEPTrt
K VALUE KNOWN TO BE
LESS THAN INDICATED
-------
STOSET
L 'JATt 75/C2/JJ
2101EA TF2101EA P003787
36 <»9 00.0 084 51 30.0
MUNUCELLU
21 7.5 MONTICELLO
r/CUMaErtLA.'JU LAKE
ti_K CREEK/otAVER CKtEK
11EHALES 2U1204
4 0000 FtET QtPTH
DATE TI"E 0£JTi
FROM OF
TO DAY FEET
73/04/17 11 00
CP ( T ) -
73/04/17 16 00
73/05/17 11 00
CP ( T ) -
73/05/17 16 00
73/06/18 11 00
CP-
73/07/17 16 00
73/08/17 11 00
CP(T)-
73/08/17 16 00
73/09/17 11 00
CPU1-
73/09/17 16 00
73/10/17 11 00
CP(T)-
73/10/17 16 00
73/11/19 10 00
cpm-
73/11/19 15 00
73/12/17 11 00
CP(T>-
73/12/17 16 00
74/01/17 11 00
CP(T)-
74/01/17 16 00
74/02/19 11 00
CP ( T ) -
74/02/19 16 00
74/03/ld 11 00
CP(T)-
74/OJ/18 16 00
OOb Jv
N02«.'«03
p^- TOTAL
MG/L
0. 155
0. 19i)
0.071
0.360
1.3BO
0.990
2.100
j.400
1.400
0.440
0.6nO
. 0.800
00625
TOT KJEL
N
MG/L
39.000
37.000
33.600
28.000
26.500
24.800
29.000
33.000
48.000
25.000
18.000
21.000
00610
NH3-N
TOTAL
MO/L
23.30
22.50
2.80
13.00
7.50
17.85
17.00
21.00
20.00
12.90
9.00
15.70
00671 00665 50051 50053
PhOS-DIS PhOS-TOT FLOw CONUUIT
ORTMO RATE FLOW-MGU
MG/L P MG/L P INST MOO MONTHLY
23.300 12.400 16.000 0.241 0.260
22.500 11.600 15.000 0.233 0.258
2.220 12.500 0.248 0.251
13.000 12.600 14.000 0.246 0.212
7.500 S.20U 8.600 0.204
0.251
17.850 18.500 19.500 0.210 0.194
17.000 4.150 4.
0.194 0.197
21.000 15.800 IB.600 0.206 0.198
20.000 14.000 16.000 0.214 0.204
12.900 11.600 12.500 0.250 0.363
9.000 14.000 14.500 0.264 0.257
15.700 13.500 13.500 0.217 0.296
-------
STOWET KETRIEVAL DATE 75/03/03
00630
DATE TIME DEPTrt N02ON03
FROM OF N-TGTAL
TO DAY FEET MG/L
21G1GA TF21G1GA P001096»
37 03 12.0 065 04 40.0
KOSSELL SWINGS
^1 7.0 KOSStLL SPRI
T/CUMbERLANO LAKE
biG LILY C^EEK
HEPALES 2141204
4 0000 FEET DEPTH
00625
TOT KJEL
N
MG/L
U0610
NH3-N
TOTAL
MG/L
00671
PrtOS-DIS
ORTHO
MG/L P
0066S
PHOS-TOT
MO/L P
50051
FLOW
rtATE
1NST MGD
50053
CONDUIT
FLOw-MGD
MONTHLY
73/04/23 09 00
73/05/30 09 00
0.014
0.140
18.COO
21.000
3.200
6.000
6.100
9.900
0.000
14.000
-------
STO«ET RETRIEVAL DATE 75/02/03
21G1NA AS2101EA P011046*
37 06 20.0 084 3'» 30.0
SOMERSET 91
21 7.5 SOMERSET
T/CUMBErtLANO LAKt
PITMAN CWEEK
11EPALES 2141204
4 0000 FEET DEPTH
U0630 00625
DATE TIME DE^Tri N02&N03 TOT KJEL
FROM OF N-TOTAL
TO DAY FEET . MG/L
73/04/16 09 00
CPU)- 0.890
73/04/17 09 00
73/05/16 09 00
CP(T>- 0.525
73/05/17 09 00
73/06/17 09 00
CP(T)- 0.640
.73/06/18 09 00
"73/07/16 09 00
CP(T>- 0.090
73/07/17 09 00
73/08/27 09 00
CP(T)- 0.066
73/08/26 09 00
73/09/17 09 00
CP(T>- 0.022
73/09/18 09 00
73/10/15 09 00
CPU)- 0.440
73/10/16 09 00
73/11/16 09 00
CPU)- 0.110
73/11/17 09 00
73/12/17 09 00
CP
------- |