U.S. ENVIRONMENTAL PROTECTION AGENCY
NATIONAL EUTROPHICATION SURVEY
WORKING PAPER SERIES
REPORT
ON
BARREN RIVER RESERVOIR
ALIBI AND BARREN COUNTIES
KENTUCKY
EPA REGION IV
WORKING PAPER No, 350
CORVALLIS ENVIRONMENTAL RESEARCH LABORATORY - CORVALLIS, OREGON
and
ENVIRONMENTAL MONITORING & SUPPORT LABORATORY - LAS VEGAS, NEVADA
699-440
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REPORT
ON
BARREN RIVER RESERVOIR
ALIEN AND BARREN COUNTIES
KENTUCKY
EPA EGION IV
WORKING PAPER No, 350
WITH THE COOPERATION OF THE
KENTUCKY DEPARTMENT FOR NATURAL RESOURCES AND
ENVIRONMENTAL PROTECTION
AND THE
KENTUCKY NATIONAL GUARD
JUNE, 1977
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CONTENTS
Foreword ii
List of Kentucky Reservoirs iv
Lake and Drainage Area Map v
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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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 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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m
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. Op KENTUCKY
NAME
Bark! ey
Barren River
Cumberland
Dale Hollow
Herrington
Kentucky
COUNTY
Lyon, Trigg, KY;
Cheatham, Montgomery,
Stewart, TN
Allen, Barren
Clinton, Pulaski, Russell,
Wayne
Clinton, Cumberland, KY;
Clay, Oyerton, Pickett, TN
Boyler, (-jarrard, Mercer
Ca.lloway, Livingston, Lyon,
Marshall, Trigg, KY;
Benton, Decatur, Henry,
Houston, Humphreys, Perry,
Stewart, TN
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(1 I"* BARREN
RIVER
RESERVOIR
KENTUCKY
TENNESSEE
Hoysville
Lafayette „ \
BARREN RIVER
RESERVOIR
(S> Tributary Sampling Site
X Lake Sampling Site
Sewage Treatment Facility
Drainage Area Boundary
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BARREN RIVER RESERVOIR
STORE! NO. 2105
CONCLUSIONS
A. Trophic Condition:
Survey data indicate Barren River Reservoir is eutrophic;
i.e., well-supplied with nutrients and productive. Whether
nutrient enrichment is beneficial or deleterious depends on the
actual or potential effect on the uses of the water body. In
this regard, personnel of the Kentucky Department for Natural
Resources and Environmental Protection have indicated there is
no known impairment of the designated beneficial uses of Barren
River Reservoir.
This water body ranked third in overall trophic quality when
the five Kentucky reservoirs sampled in 1973 were compared using
a combination of six water quality parameters*. Two of the reser-
voirs had less median total phosphorus, median orthophosphorus,
and median inorganic nitrogen; three had greater mean Secchi disc
transparency; and two had less mean chlorophyll a_. Marked depres-
sion or depletion of dissolved oxygen with depth occurred at seven
of the 11 sampling stations in August, and depletion at depth
occurred at station 2 in October.
Survey limnologists did not observe any nuisance conditions
during sampling visits.
B. Rate-Limiting Nutrient:
The algal assay results indicate the reservoir was phosphorus
* See Appendix A.
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2
limited at the time the samples were collected (05/18/73). The
reservoir data indicate phosphorus limitation at all sampling
times; i.e., all of the mean N/P mean ratios were 30/1 or greater,
and phosphorus limitation would be expected. Possible exceptions
to phosphorus limitation were stations 5, 6, and 7 in October
when the mean N/P ratios were 13/1 (borderline nitrogen limitation).
C. Nutrient Controllability:
1. Point sources—During the sampling year, point-source
phosphorus contributions amounted to at least 34.9% of the total
input to the reservoir. However, the apparent phosphorus export
rate of the South Fork at station B-2 was a very high 333 kg/km2/yr
or nearly 24 times the rate at station B-l about four kilometers
upstream (see page lij and map, page v). The magnitude of the
increase between the two sampling sites is indicative of a signifi-
cant intervening source of phosphorus other than the Glasgow waste-
water treatment plant, and the Kentucky Department for Natural
Resources and Environmental Protection is planning to conduct an
intensive survey of that segment of the South Fork drainage in the
spring of 1978 to determine the cause(s) of the excessive phosphorus
export rate (Jett, 1977).
The phosphorus loading of 1.90 g/m2 measured during the
sampling year is nearly twice that proposed by Vollenweider (Vollen-
weider and Dillon, 1974) as a eutrophic loading. While even com-
plete removal of phosphorus at the listed point sources would still
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3
leave a loading somewhat in excess of a eutrophic loading, the
reservoir is phosphorus limited, and it seems likely that a high
degree of point-source phosphorus control would result in an
improved trophic condition of the reservoir, particularly if a
large part of the excessive phosphorus export of the South Fork
proves to be controllable.
2. Non-point sources—The apparent phosphorus contribution
of non-point sources amounted to 65.1% of the total reaching the
reservoir. The gaged tributaries contributed a total of 54.7% and
ranged from 21.6% (South Fork at B-2) to 0.2% (Trace Creek). The
ungaged tributaries contributed an estimated 9.5% of the total
phosphorus load.
Note that the South Fork at station B-2, with a drainage area
of 50.0 km2, contributed more phosphorus to the reservoir than
the Barren River which has a drainage area of 995.1 km2. The high
export rate of the South Fork may have resulted from point source
impact(s).
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II. RESERVOIR AND DRAINAGE BASIN CHARACTERISTICS1"
A. Morphemetry:
1. Surface area: 40.47 kilometers2.
2. Mean depth: 5.8 meters.
3. Maximum depth: > 18.6 meters.
4. Volume: 234.708 x 106 rn3.
5. Mean hydraulic retention time: 81 days.
B. Tributary and Outlet:
(See Appendix C for flow data)
1. Tributaries -
Drainage Mean flow
Name area (km2)* (m3/sec)*
Barren River 997.1 14.08
Beaver Creek 177.4 2.43
Huggins Branch** (4.9) (0.06)
South Fork (B-l)** (33.2) (0.44)
South Fork (B-2) 50.0 0.67
Skaggs Creek 365.2 5.07
Glover Creek 27.7 0.37
Trace Creek 13.3 0.18
Rhoden Creek 25.8 0.34
Long Creek 181.3 2.49
Minor tributaries &
immediate drainage - 556.3 7.79
Totals 2,394.1 33.42
2. Outlet -
Barren River 2,434.6*** 33.42***
t Table of metric conversions—Appendix B.
tt At seasonal (summer) pool level; Jett, 1974.
* For limits of accuracy, see Working Paper No. 175, "...Survey Methods,
1973-1976".
** Areas and flows included in area and flow of South Fork at station B-2
(see map, page v).
*** Includes area of reservoir; outflow adjusted to equal sum of inflows.
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5
C. Precipitation*:
1. Year of sampling: 153.9 centimeters.
2. Mean annual: 119.3 centimeters.
See Working Paper No. 175.
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6
III. WATER QUALITY SUMMARY
Barren River Reservoir was sampled three times in 1973 by means of
a pontoon-equipped Huey helicopter. Samples for physical and chemical
paremeters were collected from one or more depths at eleven stations on
the reservoir in May and August and from ten stations in October (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, three 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 18.6 meters
at station 1, 16.8 meters at station 2, 17.4 meters at station 3, 14.3
meters at station 4, 10.7 meters at station 5, 6.1 meters at station 6,
7.0 meters at station 7, 8.5 meters at station 8, 13.7 meters at station
9, 12.2 meters at station 10, and 8.5 meters at station 11.
The sampling results are presented in full in Appendix D and are
summarized in the following table.
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PARAMETER
TEMP (C)
OISS OXY (MG/L>
CNDCTVY (MCROMO)
PH (STAND UNITS)
TOT ALK (MG/L)
TOT P (MG/L)
ORTHO P (MG/L)
N02»N03 (MG/L)
AMMONIA (MG/L)
KJEL N (MG/L)
INORG N (MG/L)
TOTAL N (MG/L)
CHLRPYL A (UG/L)
SECCHI (METERS)
A. SUMMARY OF PHYSICAL AND
1ST SAMPLING ( 5/18/73)
11 SITES
RANGE MEAN MEDIAN
14.8 - 20.5 18.2 18.6
3.0 - 12.1 7.1 6.6
CHEMICAL CHARACTERISTICS FOK BARREN RIVER RESERVOIR
STORET CODE 2105
7.5
60.
0.012
0.002
0.200
0.020
0.200
0.380
0.700
3.1
0.6
8.8
- 132.
- 0.239
- 0.122
- 3.730
- 0.370
- 0.800
- 3.890
- 4.330
- 19.6
2.1
8.0
84.
0.043
0.010
0.764
0.076
0.441
0.839
1.205
7.5
1.4
7.9
81.
0.027
0.003
0.630
0.060
0.400
0.680
1.025
6.9
1.4
MEAN MEDIAN
26.7 28.1
3.9
188.
2ND SAMPLING ( 8/11/73)
11 SITES
RANGE
16.8 - 30.1
0.0 - 9.2
174. - 295.
7.3 - 9.0
65. - 125.
0.020 - 0.324
0.005 - 0.135
0.040 - 3.220
0.050 - 2.200
0.200 - 2.400
0.090 - 3.460
0.240 - 3.820
4.0
199.
8.2
81.
8.2
79.
0.055 0.033
0.013 0.008
0.080
0.193
0.234 0.110
0.645 0.600
0.427 0.220
0.838 0.660
3RD SAMPLING (10/23/73)
10 SITES
NANGE
21.4 - 29.8
0.0 - 10.0
188. - 700.
7.2 - 8.3
78. - 133.
0.015 - 0.207 0.034 0.025
0.004 - 0.013 0.007 0.006
0.030 - 0.490
0.040 - 0.560
0.200 - 0.800 0.384 0.300
0.070 - 1.050 0.208 0.175
0.240 - 1.090 0.472 0.410
MEAN
25.0
6.0
218.
7.6
88.
MEDIAN
22.0
5.7
198.
7.4
86.
0.088 0.080
0.120 0.100
8.1 - 10.6
0.6 - 1.8
9.5
1.2
9.8
1.3
2.4 - 12.9
0.4 - 1.5
7.5
1.0
7.0
0.9
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B. Biological characteristics:
1. Phytoplankton -
Sampling
Date
05/18-19/73
08/11-13/73
10/23/73
2. Chlorophyll a^ -
Sampling
Date
05/18-19/73
Dominant
Genera
1.
2.
3.
4.
5.
1.
2.
3.
4.
5.
1.
2.
3.
4.
5.
Flagellates
Stephanodiscus sp.
Melosira sp.
Nitzschia sp.
Dinobryon sp.
Other genera
Total
Raphidiopsis sp.
Lyngbya sp_.
Achnanthes SJD.
Flagellates
Cyclotella sp.
Other genera
Total
Melosira sp.
Flagellates
Qyclotella sp.
Dactyl ococcopsis sp,
Raphidiopsis sp.
Other genera
Algal Units
per ml
4,402
2,105
2,074
638
383
861
10,463
9,775
1,
1,
777
333
889
207
563
14,544
1
149
938
181
181
151
772
Total
Station
Number
1
2
3
4
5
6
7
8
9
10
11
3,372
Chlorophyll a
(ug/l)
3.1
3.7
4.3
5.6
10.9
19.6
8.4
6.9
7.0
3.1
10.4
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Sampling
Date
08/11-13/73
C.
Station
Number
1
2
3
4
5
6
7
8
9
10
11
1
2
3
4
5
6
7
8
9
10
11
Limiting Nutrient Study:
1. Autoclaved, filtered, and nutrient spiked -
a. Stations 1, 2, 3, and 4 -
10/23/73
Spike (mg/1)
Control
0.050 P
0.050 P + 1.0 N
1.0 N
Ortho P
Cone, (mg/1)
0.012
0.062
0.062
0.012
b. Stations 5, 6, and 7 -
Spike (mg/1)
Control
0.050 P
0.050 P + 1.0 N
1.0 N
Ortho P
Cone, (mg/1)
0.040
0.090
0.090
0.040
Inorganic N
Cone, (mg/1)
0.716
0.716
1.716
1.716
Inorganic N
Cone, (mg/1)
1.104
1.104
2.104
2.104
Chlorophyll
(ug/D
9.2
9.8
10.1
10.4
10.6
8.9
10.6
9.8
8.5
8.4
8.1
2.4
3.4
5.9
5.7
10.9
8.5
7.0
10.6
12.9
Maximum yield
(mg/1-dry wt.)
0.1
18.2
19.2
0.1
Maximum yield
(mg/1-dry wt.)
15.8
25.0
26.8
15.0
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0.008
0.058
0.058
0.008
0.672
0.672
1.672
1.672
0.1
14.8
19.5
0.1
10
c. Stations 8, 9, 10, and 11 -
Ortho P Inorganic N Maximum yield
Spike (mg/1) Cone, (mg/1) Cone, (mg/1) (mg/1 -dry__wt..)
Control
0.050 P
0.050 P + 1.0 N
1.0 N
2. Discussion -
The control yields of the assay alga, Selenastrum capri-
cornutum, indicate that the potential primary productivity
at stations 1, 2, 3, and 4, and stations 8, 9, 10, and
11, was low at the time the samples were collected (May, 1973).
However, the control yield of the sample from stations 5, 6,
and 7 indicates a high potential primary productivity; this
most likely is an indication of the proximity of upstream
nutrient sources. The results also indicate the reservoir
was phosphorus limited at that time. Note the increases in
yields with the addition of phosphorus and the lack of signifi-
cant change in yields with the addition of nitrogen alone.
The reservoir data indicate phosphorus limitation at all
sampling times, with the possible exception of stations 5, 6,
and 7 in October, 1973, when the mean inorganic nitrogen/ortho-
phosphorus ratios were 13/1 at those stations (borderline
nitrogen limitation).
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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 January and February when extra 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.
In this report, nutrient loads for sampled tributaries were deter-
mined by using a modification of a U.S. Geological Survey computer
program for calculating stream loadings*. Nutrient loads shown are
those measured minus point-source loads, if any.
Nutrient loadings for 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 A-l, B-l, C-l, D-l, E-l,
F-l, G-l, and H-l and multiplying the means by the ZZ area in km2.
The operators of the Glasgow and Tompkinsville wastewater treatment
plants provided monthly effluent samples and corresponding flow data.
* See Working Paper No. 175.
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A. Waste Sources:
1. Known municipal* -
Pop. Mean Flow Receiving
Name Served Treatment (m3/d) Water
Tompkinsville 2,207 act. sludge 761.6 Curtis Br. of
Mill Cr.
Glasgow** 10,000 tr. filter 10,912.2 S. Fk., Beaver Cr.
2. Known industrial - None with separate discharges.
* Treatment plant questionnaires.
** Approximately 50% of the waste load contributed by industries.
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13
B. Annual Total Phosphorus Loading - Average Year:
1. Inputs -
kg P/ % of
Source yr total
a. Tributaries (non-point load) -
Barren River 15,245 19.8
Beaver Creek 3,360 4.4
South Fork (B-2) 16,655 21.6
Skaggs Creek 4,060 5.3
Glover Creek 405 0.5
Trace Creek 170 0.2
Rhoden Creek 330 0.4
Long Creek 1,915 2.5
b. Minor tributaries & immediate
drainage (non-point load) - 7,300 9.5
c. Known municipal STP's -
Tompkinsville 2,945 3.8
Glasgow 23,975 31.1
d. Septic tanks* - 20 <0.1
e. Known industrial - None
f. Direct precipitation** - 710 0.9
Total 77,090 100.0
2. Outputs -
Reservoir outlet - Barren River 50,720
3. Net annual P accumulation - 26,370 kg.
* Estimate based on 65 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) -
Barren River 661,915 37.6
Beaver Creek 158,530 9.0
South Fork (B-2) 59,610 3.4
Skaggs Creek 267,665 15.2
Glover Creek 11,915 0.7
Trace Creek 6,660 0.4
Rhoden Creek 11,800 0.7
Long Creek 115,635 6.6
b. Minor tributaries & immediate
drainage (non-point load) - 354,295 20.1
c. Known municipal STP's -
Tompkinsville 1,655 < 0.1
Glasgow 65,640 3.7
d. Septic tanks* - 695 < 0.1
e. Known industrial - None
f. Direct precipitation** - 43.690 2.5
Total 1,759,705 100.0
2. Outputs -
Reservoir outlet - Barren River 1,472,500
3. Net annual N accumulation - 287,205 kg.
* Estimate based on 65 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:
Tri butary kg P/km2/yr kg N/km2/yr
Beaver Creek 19 894
South Fork (B-l) 14 786
South Fork (B-2)* 333 1,192
Muggins Branch 9 656
Skaggs Creek 11 733
Glover Creek 15 430
Trace Creek 13 501
Rhoden Creek 13 457
Long Creek 11 638
Barren River 15 664
* This excessively high export may be due to point sources
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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 1.90 0.65 43.5 7.1
Vollenweider phosphorus loadings
(g/m2/yr) based on mean depth and mean
hydraulic retention time of Barren River Reservoir:
"Dangerous" (eutrophic loading) 0.98
"Permissible" (oligotrophic loading) 0.49
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17
V. LITERATURE REVIEWED
Jett, Shelby, 1974. Personal communication (reservoir morphometry).
Dept. for Nat. Resources & Env. Prot., Frankfort.
1977. Personal communication (planned segment survey
of the South Fork). Dept. for Nat. Resources & Env. Prot.,
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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LAKH DATA TO BE USED IN RANKINGS
LAKE
COOE LAKE NAME
2101 LAKE CuMdE«L«NU-
2102 DALE HOLLOW RESERVOIR
£1103 HERRINGTON LAKE
210*» KENTUCKY LAKE
BARKEN RIVER RESERVOIR
MEDIAN
TOTAL P
0.016
0.010
0.07*
0.072
0.027
MEDIAN
INOKG N
0.330
0.270
0.550
0.520
0.460
500-
MEAN SEC
432. 3B1
330.000
442.667
461.972
452.594
MEAN
CHLOKA
3.805
3.594
14.908
9.089
8.216
15-
MIN DO
14.900
14.800
14.900
12.600
14.900
MEDIAN
DISS P
0.007
0.005
0.047
0.030
0.006
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PERCENT OH LAKES *1TH HlGhEK VALUES
LAKE
CODE LAKE NAME
INDEX
NO
2101 LAKE CUMStKLANU 60 ( 3> t>0 ( 3) 60 (3) 60 ( 3) 20 (0) 40 ( 2) 300
2102 DALE HOLLOW WESE«V01« 80 (4) 60 ( 4) bO (4) 80 ( 4> 60 ( 3) 80 ( 4) 460
2103 HEUHaNGFOf'J LAKE 0 < 0) 0 < 0) 40 ( 2) 0(0) 20 ( 0) 0(0) 60
210<« KENTUCKY LAKE 20 < A) 20 ( 1) 0 ( 0) 20 (1) 80 ( 4) 20 ( 1) 160
2i05 tiAKKEN RIVE* KESEKVOIri 40 (2) 40 < 2) 20 (1) 40 ( 2) 20 (0) 60 ( 3) 220
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LAKES RANKED HY INOLA NOSo
WANK LAKE CODE LA*L NAME INDEX NO
1 2102 DALE HOLLOW KEbEHVOIrt 460 .
2 2101 ' LAKE CUMbE^LANO 300
"J 21ob dAKKEN RWEK KESEWVOIK 220
to 2104 KENIUCKY LA^E 160
b 2103 HEKR1NGTON LAKE 60
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APPENDIX B
CONVERSION FACTORS
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CONVERSION FACTORS
Hectares x 2.471 = acres
Kilometers x 0.6214 = miles
Mstars x 3.281 -- feet
-A
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
4
Kilograms x 2.205 - pounds
Kilograms/square kilometer x 5.711 * Ibs/square mile
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APPENDIX C
TRIBUTARY FLOW DATA
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LAKE CODE 2105
TRIBUTARY FLO'« INFORMATION FOR KENTUCKY
RIVER LAKE
3/3/75
TOTAL DRAINAGE AREA OK LAKE(SO KM) 2434.6
SUfl-DKAliMAGt
TRIBUTARY AREA(SC) KM)
JAN
FE8
MAR
NORMALIZED FLOttfS(CMb)
APR MAY JUN JUL AUO
SEP
OCT
NOV
OtC
SUMMARY
TOTAL DRAINAGE AREA OF LAKE =
SUM OF SUB-DRAINAGE AREAS =
2434.6
2432.7
TOTAL FLUw IN = 409.42
TOTAL FLOW OUT = 477.51
MEAN MONTHLY FLOWS AND DAILY FLOWS(CMS)
TRIBUTARY MONTH YEAR MEAN FLOW OAY
2105A1
210561
3
4
5
6
7
8
9
10
11
12
1
2
3
3
4
5
6
7
8
9
10
11
1?
1
2
3
73
73
73
73
73
73
73
73
73
73
74
74
7-4
73
73
73
73
73
73
73
73
73
73
74
74
74
12.54
8.44
4.73
2.04
1.47
0.76
0.24
0.42
6.91
4.42
14.92
5.44
5.75
2.32
1.53
0.«8
0.37
0.26
0.12
0.04
0.07
1.27
0.79
2.55
1.02
1.08
13
1
17
22
19
16
14
17
20
13
29
13
1
17
22
19
16
14
17
13
28
29
FLOW DAY
3.71
6.06
1.22
0.65
0,57
0.23
0.51
0.48
4.87 30
3.03 28
3.54
0.68
1.13
0.22
0.12
0.09
0.04
0.08
0.09
2.4b 20
0.85
0,65
FLOW OAY
FLOW
7.14
4.62
0.32
1.22
MEAN
2105A1
2105bl
210512
2105C1
2105D1
2105E1
2105F1
2105G1
2105H1
2105J1
2105J2
2105ZZ
177.4
33.2
50.0
4.9
365.2
27.7
13.3
25.8
181.3
997.1
2434.6
556. d
3.99
0.68
1.05
0.09
8.55
0.57
0.2to
Oo54
4.11
24.52
68.36
13.31
5.32
0.99
1.47
0.14
11.04
0.82
0.40
0.76
5.44
30.44
67.37
16.91
6.43
1.19
1.31
0.18
13.22
li.99
0.48
0.93
6.57
36.08
42.16
20.16
3.74
0.68
1.02
0.10
7.82
0.57
0.27
0.51
3.62
21. IS
31.26
11.98
2.46
0.45
0.71
0.07
5.01
O.nO
0.19
0.37
2.52
13.56
31.38
7.62
1.22
0.21
0.34
0.03
2.b3
0.18
0.03
0.16
1.25
7.53
20.84
4.11
1.08
0.19
0.23
0.03
2.24
0.16
U.08
0.15
1.10
6.20
27. 1)4
3.43
0.57
0.09
0,14
0.01
1.22
0.07
0.03
0.07
0.57
3.62
21.58
1.93
0.37
0.07
0.10
0.01
0.82
0.05
0.03
0.05
0.40
2.35
16. d8
1.27
0.27
0.05
0.07
0.01
0.57
0.04
0.02
0.04
0.27
1.64
37.07
0.88
1.22
0.22
0.34
0.03
2.52
0. 19
0.09
0.17
1.25
6.91
62.61
3.85
2.69
0.48
0.74
0.07
5.58
0.42
0.20
0.40
2.75
15.38
50.97
8. 55
2.43
0.44
0.67
0.06
5.07
0.37
0.18
0.34
2.49
14.08
39.64
7.79
-------
LAKE COOE 3105
TRIBUTARY FLOW INFORMATION FOR KENTUCKY
BARREN RIVER LAKE
3/3/75
MEAN MONTHLY FLOWS AND DAILY FLOWS(CMS)
TRIBUTARY MONTH YEAH MEAN FLOW DAY
2105B2
2105CI
210501
2105E1
3
4
5
6
7
8
9
10
11
12
1
2
3
3
A
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
f
73
73
73
73
73
73
73
73
73
73
74
74
74
73
73
73
73
73
73
73
73
73
73
74
7<»
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
7*
74
3.54
2.29
1.36
0.57
0.40
0.19
0.07
0.11
1.93
1.22
3.91
1.50
1.61
0.34
0.22
0.14
0.05
0.04
0.01
0.01
0.01
0.18
0.12
0.34
0.14
0.16
25.80
17.67
9.63
4.39
3.06
1.67
0.54
0.88
14.27
9.15
31.97
11.27
11.81
1.93
1.27
0.76
0.28
0.22
0.10
0.03
0.06
1.05
0.71
2.12
0.85
0.88
13
1
17
22
19
16
14
17
20
13
29
13
1
17
22
19
16
14
17
20
13
29
13
1
17
22
19
16
14
17
20
13
29
31
28
11
22
19
16
15
28
27
26
23
31
FLOW DAY
1.02
1.73
0.34
0.18
0.14
0.07
0.13
0.13
1.27 30
0.85 28
0.99
0.10
0.17
0.03
0.02
0.01
0.01
0.01
0.01
0.11 30
0.08 28
0.10
7.79
12.32
2.63
1.36
1.25
0.54
1.08
0.99
10.42
6.29
7.25
0.7b
1.19
0.18
0.10
0.08
0.03
0.06
11.81
2.12
0.68
1.50
0.51
FLOW DAY
FLOW
1.87
1.27
0.16
0.12
30
28
15.32
9.54
-------
TRIBUTARY FLOW INFORMATION FOR KENTUCKY
2/3/75
LAKE CODE 2105 dARRLN RIVE* LAKE
MEAN MONTHLY FLOWS AND JAILY FLOWS(CMS)
TRIBUTARY MONTH YEAK
2105F1
2105G1
2105H1
2105J1
MLAN FLOW DAY
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
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
73
73
73
73
73
73
73
73
73
73
74
74
74
FLO* DAY
0.93
0.59
0.37
0.14
0.10
0.05
0.02
0.03
0.51
0.31
0.99
0.40
0.42
1.81
1.16
0.71
0.27
0.21
0.09
0.03
0.06
0.99
0.65
2.01
0.79
0.82
12.80
8.64
4.84
2.07
1.50
0.76
0.26
0.42
7.05
4.50
15.35
5.55
5.86
70.23
49.27
260.51
12.57
8.50
4.96
1.53
2.52
39.08
25.23
91.75
31.15
32.28
31
28
11
22
19
16
15
28
27
26
23
31
31
28
22
19
16
15
28
27
26
23
31
31
28
22
19
16
15
28
27
26
23
31
31
28
22
19
16
15
28
27
23
31
0.37
0.57
0.09
0.05
0.03
0.02
0.03
5.75
0.93
0.31
0.71
0.25
0.7<»
1.08
0.09
0.07
0.03
0.06
11.19
1.95
O.t>5
1.42
0.48
5.13
8.04
0.65
0.57
0.25
0.45
79.57
13.51
4.98
9.83
3.45
28.15
45.87
3.74
3.71
1.50
2.76
441.74
75.61
54.93
19.06
FLOW DAY
FLOW
-------
TRIbUTASY FLOW INFORMATION FOR KENTUCKY
LAKE CODE 3105 dARRtN RI\/ER LAKE
MEAN MONTHLY FLOaS AND DAILY FLOwS(CMS)
TRIBUTARY MONTn YtAri MEAN FLOW DAY FLO* DAY FLOW DAY
2105J2
a/3/rs
2105ZZ
FLOW
3
4
5
6
7
8
9
10
11
12
1
2
3
3
4
5
6
7
8
9
lo
11
12
1
a
3
73
73
73
73
73
7J
73
73
73
73
74
74
74
73
73
73
73
73
73
73
73
73
73
7<*
7<*
74
17.19
60.63
97.32
56.46
39.33
9.49
10.68
32.22
54.20
89.20
90. bO
129.95
51.90
39.36
27.07
14.61
6.65
4.70
2.63
0.82
1.36
21.83
14.05
49.84
17.24
18.01
13
1
17
22
19
16
15
28
20
13
29
101.66
12.52
53.80
20.64
13.45
3.82
30.02
22.57
103.92 30 134.79
131.11 26 121.20
4.90
-------
APPENDIX D
PHYSICAL and CHEMICAL DATA
-------
RETRIEVAL DATE 75/01/27
210501
36 53 28.0 086 07 17.0
BARREN RIVER RESERVOIR
21009 KENTUCKY
11EPALES
DATE
FROM
Tu
73/05/18
73/08/11
73/10/23
DATE
FROM
TO
73/05/18
73/08/11
73/10/23
TIME DEPTH
OF
DAY FEET
09 55 0000
09 55 0004
09 55 0024
09 55 0040
09 55 0056
16 20 0000
16 20 0005
16 20 0015
16 20 0025
16 20 0035
16 20 0045
16 20 0061
10 20 OOGO
10 20 0005
10 20 0015
10 20 0035
10 20 0045
TIME DEPTH
OF
DAY FEET
09 55 0000
09 55 0004
09 55 0024
09 55 0040
09 55 0056
16 20 0000
16 20 0005
16 20 0015
16 20 0025
16 20 0035
16 20 0045
16 20 0061
10 20 0000
10 20 0005
10 20 0015
10 20 0035
10 20 0045
00010
WATER
TEMP
CENT
18.8
18.8
18.5
17.2
14.8
29.4
29.4
28.5
25.2
23.2
20.9
16.8
22.0
22.0
22.0
21.9
21. d
00665
PHOS-TOT
MG/L P
0.017
0.015
0.020
0.012
0.028
0.022
0.022
0.033
0.024
0.026
0.026
0.067
0.016
u.016
0.018
0.025
0.025
00300
DO
MG/L
9.5
9.4
7.8
5.3
8.4
3.0
0.1
0.0
0.0
0.2
5.4
4.4
4.0
4.2
32217
CHLRPHYL
A
UG/L
3.1
9.2
2.4
00077 00094
TRANSP CNDUCTVY
SECCH1 FIELD
INCHES MICROMHO
84 190
180
180
185
208
72 176
177
175
210
192
182
192
60 195
195
195
195
196
3
00400
PH
SU
7.50
8.00
8.00
7.90
7.70
8.30
8.20
8.20
8.00
7.90
7.80
7.60
7.30
7.30
7.30
7.30
7.30
00410
T 6LK
CAC03
MG/L
70
70
69
74
84
66
66
88
85
85
83
95
79
78
80
81
82
2111202
0060
00610
NH3-N
TOTAL
MG/L
0.040
0.020
0.030
0.040
0.030
0.100
0.080
0.180
0.240
0.240
0.390
0.860
0.180
0.170
0.170
0.180
0.220
FEET DEPTH
00625
TOT KJEL
N
MG/L
0.500
0.400
0.300
0.300
0.300
0.800
0.300
0.500
0.600
0.400
0.700
1.200
0.800
0.300
0.300
0.300
0.400
00630
N02&N03
N-TOTAL
MG/L
0.620
0.620
0.620
0.670
0.850
0.100
0.090
0.060
0.040
0.050
0.110
0.080
0.110
0.110
0.100
0.110
0.100
00671
PHOS-UIS
ORTriO
MG/L P
0.005
0.004
0.003
0.004
0.006
0.010
0.012
0.009
0.008
0.009
0.009
0.006
0.008
0.006
0.006
0.012
0.009
-------
STORE! RETRIEVAL DATE 75/01/37
310502
36 54 02.0 086 05 47.0
BARREN RIVER RESERVOIR
21009 KENTUCKY
11EPALES
DATE
FROM
TO
73/05/18
73/08/11
73/10/23
DATE
FROM
TO
73/05/18
73/08/11
73/10/23
TIME DEPTH
OF
DAY FEET
10 35 0000
10 35 0004
10 35 0024
10 35 0030
10 35 0035
10 35 0040
10 35 0045
10 35 0055
16 25 0000
16 25 0005
16 25 0015
16 25 0025
16 25 0038
10 45 0000
10 45 0005
10 45 0015
10 45 0036
TIME DEPTH
OF
DAY FEET
10 35 0000
10 35 0004
10 35 0024
10 35 0030
10 35 0035
10 35 0040
10 35 0045
10 35 0055
16 25 0000
16 25 0005
16 25 OOlb
16 25 0025
16 25 0038
10 45 0000
10 45 0005
10 45 0015
10 45 0036
00010
WATER
TEMP
CENT
19.1
19.1
18.8
18.0
17.7
17.3
16.6
15.5
29.5
29.4
28.7
25.2
22.7
21.9
21.8
21.7
21. S
00665
PHOS-TOT
MG/L P
0.046
0.017
0.016
0.023
0.032
0.025
0.029
0.026
0.020
0.026
0.024
0.033
0.034
0.016
0.017
0.01s
0.025
00300
DO
MG/L
9.9
9.1
7.0
5.6
5.8
5.4
4.0
b.6
7.0
0.5
1.0
5.9
b.6
0.0
32217
CHLRPHYL
A
UG/L
3.7
9.8
3.4
00077 00094
TRANSP CNDUCTVY
SECCHI FIELD
INCHES MICROMHO
84 180
182
192
198
219
200
200
219
64 179
178
17fo
205
203
48 194
194
195
196
3
00400
PH
5U
8.00
8.20
8.00
7.90
7.70
7.70
7.60
7.60
8.20
8.30
7.90
8.10
8.10
7.40
7.40
7.40
7.40
00410
T ALK
CAC03
MG/L
71
72
72
78
89
85
84
87
68
67
69
92
93
85
87
90
90
2111202
0060
00610
NH3-N
TOTAL
MG/L
0.040
0.020
0.040
0.060
0.120
0.120
0.120
0.100
0.090
0.080
0.120
0.480
0.310
0.150
0.140
0.150
0.150
FEET DEPTH
00625
TOT KJEL
N
MG/L
0.400
0.400
0.400
O.SOO
0.600
0.200
0.200
0.200
0.600
0.400
0.400
0.800
0.800
0.300
0.300
0.200
0.300
00630
N02&N03
N-TOTAL
MG/L
0.610
0.600
0.590
0.670
0.790
0.730
0.710
0.750
0.060
0.100
0.120
0.050
0.050
0.090
0.090
0.090
0.080
00671
PHOS-DIS
ORTHO
MG/L P
0.003
0.006
0.004
0.006
0.005
0.004
0.002
0.002
0.005
0.009
0.007
0.006
0.009
0.004
0.005
0.006
0.006
-------
STORET RETRIEVAL DATE 75/01/37
210S03
36 53 01.0 086 04 36.0
BARREN RIVER RESERVOIR
21009 KENTUCKY
DATE
FROM
TO
73/05/18
73/08/13
73/10/23
DATE
FROM
TO
TIME DEPTH
OF
DAY FEET
13 25 0000
13 25 0004
13 25 0024
13 25 0040
13 25 0057
09 40 0000
09 40 0005
09 40 0015
09 40 0025
09 40 0033
11 05 0000
11 05 0005
11 05 0015
11 05 0036
TIME DEPTH
OF
DAY FEET
00010
*ATER
TEMP
CENT
19.7
19.7
18.5
16.6
15.3
28.6
28.4
28.3
24.9
23.0
21.4
00665
PHOS-TOT
MG/L P
00300
DO
MG/L
10.0
8.2
5.1
3.1
7.8
7.2
0.6
O.H
7.6
5.6
4.6
32217
CrlLRPHYL
A
UG/L
11EPALES
3
00077 00094 00400 00<*10
TRANSP CNOUCTVY
SECCHI FIELO
INCHES MICROMHO
72 180
176
176
183
198
52 181
183
184
192
200
45 195
193
194
209
PH
su
8.
8.
8.
7.
7.
9.
8.
8.
8.
7.
7.
7.
7.
7.
T ALK
CAC03
MG/L
00
20
10
90
70
00
80
40
00
90
60
50
50
30
73
71
70
73
80
71
71
68
79
86
89
87
88
87
2111202
0061 FEET DEPTH
00610 00625 00630
NH3-N
TOTAL
MG/L
0.040
0.030
0.040
0.080
0.090
0.090
0.050
0.060
0.200
0.500
0.100
0.080
0.100
0.040
TOT KJEL
N
MG/L
0.300
0.200
0.200
0.200
0.300
1.400
0.700
0.700
0.800
1.400
0.300
0.200K
0.200K
0.600
N02&N03
N-TOTAL
MG/L
0.510
0.500
0.530
0.640
0.700
0.060
0.040
0.060
0.100
0.090
0.080
0.080
0.070
0.080
00671
PHOS-DIS
ORTHO
MG/L P
0.007
0.002
0.002
0.002
0.013
0.006
0.008
0.007
0.007
0.005
0.004
0.005
0.005
0.005
K VALUE KNOWN TO BE
73/05/18
73/08/13
73/10/23
13 25 0000
13 25 0004
13 25 0024
13 25 0040
13 25 0057
09 40 0000
09 40 0005
09 40 0015
09 40 0025
09 40 0033
11 05 0000
11 05 0005
11 05 0015
11 05 0036
0.026
0.020
0.021
0.026
0.035
U.024
0.024
0.025
0.026
O.OtoO
0.026
0.023
0.022
0.207
4.3
10.1
5.9
LESS THAN
INDICATED
-------
STORET RETRIEVAL DATE 75/01/37
210504
36 54 10.0 086 03 58.0
BARKEN RIVER RESERVOIR
21009 KENTUCKY
DATE
FROM
TO
73/05/18
73/08/13
73/10/23
DATE
FROM
TO
73/05/18
73/08/13
7J/10/23
TIME DEPTH
OF
DAY FEET
14 05 0000
14 05 0004
14 05 0017
14 05 0020
14 05 0025
14 05 0035
14 05 0047
10 05 0000
10 05 0005
10 05 0015
10 05 0025
10 05 0035
10 05 0046
11 55 0000
11 55 0005
11 55 0015
11 55 0033
TIME DEPTH
OF
DAY FEET
14 05 0000
14 05 0004
14 05 0017
14 05 0020
14 05 0025
14 05 0035
14 05 0047
10 05 0000
10 OS 0005
10 OS 0015
10 05 0025
10 05 0035
10 05 0046
11 55 0000
11 55 0005
11 55 0015
11 55 0033
00010
WATER
TtMP
CENT
19.4
19.5
19.0
19.0
18.1
17.4
16.7
28.9
28.8
28.7
25.4
23.5
20.7
00665
PHOS-TOT
MG/L P
0.023
0.027
0.017
0.017
0.038
0.057
0.065
0.022
0.026
0.024
0.048
0.089
0.133
0.025
0.025
0.025
0.034
00300
DO
MG/L
10.3
9.1
8.8
5.1
3.5
3.0
7.6
6.7
0.2
0.2
0.2
5.8
5.4
4.6
32217
CrILRPHYL
A
UG/L
5.6
10.4
5.7
00077 00094
TRANSP CNDUCTVY
SECCHI FIELD
INCHES MICROMHO
70 211
210
202
220
221
219
238
54 180
180
182
240
262
255
36 204
203
203
212
11EPALES
3
00400 00410
PH
su
8.10
8.30
8.30
8.00
7.80
7.70
7.60
8.50
8.60
7.80
7.40
7.30
8.20
7.40
7.40
7.40
7.30
T ALK
CAC03
MG/L
85
86
78
77
84
81
92
68
69
66
97
113
125
96
83
82
84
2111202
0051 FEET DEPTH
00610 00625 00630
NH3-N
TOTAL
MG/L
0.080
0.020
0.040
0.040
0.150
0.230
0.370
0.070
0.070
0.070
0.290
0.860
2.200
0.150
0.140
0.150
0.180
TOT KJEL
N
MG/L
0.300
0.300
0.300
0.300
0.400
0.600
0.800
1.200
1.200
1.000
0.500
1.000
2.400
0.500
0.500
0.400
0.500
N02&N03
N-TOTAL
MG/L
0.680
0.650
0.640
0.650
0.820
0.880
0.700
0.050
0.100
0.050
0.150
0.060
0.120
0.080
0.070
0.070
0.060
00671
PHOS-DIS
ORTHO
MG/L P
0.007
0.006
0.003
0.003
0.003
0.010
0.012
0.011
0.010
0.007
0.006
0.005
0.010
0.004
0.007
0.007
0.006
-------
sTORET RETRIEVAL DATE 75/01/37
210505
36 55 25.0 086 02 45.0
BARREN HIVtH RESERVOIR
21009 KENTUCKY
DATE
FROM
TO
73/05/18
73/08/13
73/10/23
DATE
FROM
TO
73/05/18
73/08/13
73/10/23
TIME DEPTH
OF
DAY FEET
15 00 0000
15 00 0004
15 00 0011
15 00 0022
15 00 0030
10 30 0000
10 30 0005
10 30 0015
10 30 0025
10 30 0035
12 10 0000
12 10 0005
12 10 0017
TIME DEPTH
OF
DAY FEET
15 00 0000
15 00 0004
15 00 0011
IS 00 0022
15 00 0030
10 30 0000
10 30 0005
10 30 0015
10 30 0025
10 30 0035
12 10 0000
12 10 0005
12 10 0017
00010
WATER
TEMP
CENT
19.6
19.6
19. 1
18.5
17.1
28.9
28.8
28.3
25.1
24.2
00665
PHOS-TOT
MG/L P
0.027
0.027
O.OJ9
0.042
0.053
0.036
0.039
0.046
0.165
0.1*7
0.038
0.030
0.055
00300
DO
MG/L
12.1
7.9
6.0
5.9
7.6
4.8
0.2
1.0
8.2
7.0
32217
CHLRPHYL
A
UG/L
10.9
10.6
10.9
00077 00094
TRANSP CNDUCTVY
SECCHI FIELD
INCHES MICROMHO
3b 238
238
239
238
250
52 181
181
202
253
236
33 20b
205
223
11EPALES
3
00400 004lu
PH
SU
8
8
8
8
7
8
8
8
7
7
7
7
7
.20
.50
.20
.00
.80
.50
.50
.10
.60
.60
.90
.90
.80
T ALK
CAC03
MG/L
93
92
96
95
104
66
b7
67
97
89
83
82
88
2111202
0034 FEET DEPTH
00610 00625 00630
NH3-N
TOTAL
MG/L
0.060
0.060
0.070
0.120
0.180
0.080
0.050
0.090
0.380
0.290
0.080
0.070
0.080
TOT KJEL
N
MG/L
0.600
0.400
0.400
0.400
0.500
0.600
0.200
0.300
0.600
0.700
0.600
0.400
0.600
N026.N03
.N-TOTAL
MG/L
0.650
0.650
0.670
0.820
0.200
0.060
0.040
0.090
0.530
0.610
0.060
0.060
0.040
00671
PHOS-DIS
ORTHO
MG/L P
0.005
0.007
0.003
0.003
0.007
0.005
0.009
0.011
0.035
0.023
0.006
0.013
0.012
-------
STORET RETRIEVAL DATE 75/01/37
310506
36 57 lb.0 036 00 54.0
bARREN RIVER RESERVOIR
21009 KENTUCKY
11EPALES
3
2111202
0022 FEET
DEPTH
DATE TIME DEPTH
FROM OF
TO DAY FEET
73/05/19 09 40 0000
09 40 0004
09 40 0010
09 40 0015
09 40 0030
73/08/13 10 55 0000
10 55 0005
10 55 0013
00010
*ATER
TEMP
CENT
19. d
19. 4
15.3
15.0
14.9
29.4
27.8
23.7
00300
DO
MG/L
10.8
7.0
6.4
6.4
7.0
5.4
00077
TRANSH CI-
SECCHI FIELD
INCHES M]
24
24
94
TVY
1
MHO
250
340
340
340
340
190
241
295
00400
HH
SU
8.80
8.00
7.80
7.80
7.80
8.70
8.40
8.50
00410
T ALK
CAC03
MG/L
95
98
130
131
132
65
81
110
00610
NH3-N
TOTAL
MG/L
0.040
0.050
0.140
0.160
0.160
0.070
0.120
0.240
00625
TOT KJEL
N
MG/L
0.800
0.600
0.600
0.600
0.800
0.700
0.700
0.600
00630
N02&N03
N-TOTAL
MG/L
0.660
0.750
3.300
3.730
3.220
0.070
0.440
3.220
00671
PHOS-DIS
ORTHO
MG/L P
0.006
0.021
0.090
0.122
0.119
0.008
0.075
0.135
0066b 32217
DATE TIME. DEPTH PHOS-TOT CHLRPHYL
FROM OF A
TO DAY FEET MG/L P UG/L
73/U5/19 09 40 0000 0.068 19.6
09 40 0004 0.198
09 40 0010 0.200
09 40 0015 0.233
09 40 0020 0.239
73/08/13 10 55 0000 O.OB6 8.9
10 55 0005 0.189
10 55 0013 0.324
K VALUE l\NO*N TO bE
LESS THAN INDICATED
-------
STORE! RETRIEVAL DATE 7S/01/27
210507
36 54 55.0 085 59 57.0
BARREN RIVER RESERVOIR
21009 KENTUCKY
00010
DATE TIME DEPTH *ATER
FROM OF TEMP
TO DAY FEET CENT
73/05/19 10 25 0000
10 25 0004
10 25 0010
10 25 0015
10 25 0023
73/08/13 11 15 0000
11 15 0005
11 15 0015
73/10/23 12 40 0000
20.5
20.3
19.6
17.3
16.2
29.1
29.0
24.7
11EPALES
3
00300
DO
MG/L
10.6
8.6
6.8
6.8
7.8
4.8
9.3
00077
TRANSP
SECCHI
INCHES
40
29
24
00094
CNDUCTVY
FIELD
M1CROMHO
240
240
200
240
280
185
185
236
00400
PH
SU
8.60
8.20
8.60
8.30
7.90
8.60
8.60
7.90
8.30
00410
T ALK
CAC03
MG/L
93
93
94
95
110
66
68
94
91
2111202
0022 FEET DEPTH
00610
NH3-N
TOTAL
MG/L
0.050
0.060
0.040
0.060
0.040
0.060
0.060
0.120
0.040
00&25
TOT KJEL
N
MG/L
0.600
0.600
0.500
0.600
0.400
0.400
0.200
0.400
0.500
00630
IM02&N03
N-TOTAL
MG/L
0.530
0.530
0.530
0.500
0.790
0.060
0.050
0.600
0.030
00671
PHOS-DIS
ORTHO
MG/L P
0.011
0.006
0.005
0.002K
0.003
0.008
0.011
0.020
0.007
DATE TIME DEPTh-
FROM OF
TO DAY FEET
73/05/19 10 25 0000
10 25 0004
10 25 0010
10 25 0015
10 25 0023
73/OB/13 11 15 0000
11 15 0005
11 15 0015
73/10/23 12 40 0000
0.045
0.04B
0.037
0.028
0.039
0.043
0.046
0.112
0.03b
0665
S-TOT
/L P
0.045
0.048
0.037
0.028
0.039
0.043
0.046
0.112
0.03fa
32217
CHLRPHYL
A
UG/L
8.4
10.6
K VALUE KNOWN TO BE
LESS THAN INDICATED
-------
STOKET RETRIEVAL DATE 75/01/27
210508
36 51 50.0 086 02 37.0
dARREN RIVtK
21009 KENTUCKY
DATE
FROM
TO
73/05/19
73/08/13
73/10/23
TIME DEPTH
OF
DAY FEET
11 00 0000
11 00 0004
11 00 0015
11 00 002U
13 35 0000
13 35 0005
13 35 0015
12 45 0000
12 45 0005
00010
wATER
TEMP
CENT
19.9
19.8
18.7
16.2
29.4
29.1
27.6
29. a
29.8
00300 00077 00094
DO TKANSP CNDUCTVY
SECCHI FIELD
MG/L INCHES MiCROMHO
9.0
6.6
6.6
9.2
8.0
9.0
48
60
37
190
190
220
220
174
174
184
190
188
11EPALES
3
00400
PH
su
8.20
8.20
7.80
7.70
8.60
8.70
8.00
8.20
3.10
00410
T ALK
CAC03
MG/L
78
78
96
97
72
72
79
85
86
2111202
0032
00610
NH3-N
TOTAL
MG/L
0.030
0.030
0.060
0.080
0.070
0.050
0.120
0.0 tO
0.040
FEET DEPTH
00625
TOT KJEL
N
MG/L
0.500
0.400
0.300
0.500
0.400
0.200
0.300
0.500
0.300
00630
N02&N03
N-TOTAL
MG/L
0.540
0.520
0.830
0.850
0.060
0.050
0.100
0.050
0.050
00671
PHOS-DIS
ORTHO
MG/L P
0.004
0.002
0.002K
0.002
0.007
0.009
0.008
0.006
0.006
00665 32217
DATE TIME DEPTH PHOS-TOT CHLRPHYL
FROM OF A
TO DAY FEET MG/L P UG/L
73/05/19 11 00 0000 0.025 6.9
11 00 0004 0.022
11 00 0015 0.029
11 00 0028 U.036
73/08/13 13 35 0000 0.027 9.8
13 35 0005 0.027
13 35 OOlb 0.050
73/10/23 12 45 0000 0.031 8.5
12 45 0005 0.030
K VALUE KNOWN TO BE
LESS TH*N INDICATED
-------
STORET RETRIEVAL DATE 75/01/27
210509
36 50 40.U 086 04 20.0
BARREN RIVER RESERVOIR
21009 KENTUCKY
DATE
FROM
TO
73/05/19
73/OB/13
73/10/23
DATE
FROM
TO
73/05/19
73/08/13
73/10/23
TIME DEPTH
OF
DAY FEET
13 20 0000
13 20 0004
13 20 0015
13 20 0030
13 20 0045
13 55 0000
13 55 0005
13 55 0015
13 55 0025
13 55 0040
12 55 0000
12 55 0005
12 55 0015
12 55 0033
TIME DEPTH
OF
DAY FEET
13 20 0000
13 20 0004
13 20 0015
13 20 0030
13 20 0045
13 55 0000
13 55 0005
13 55 0015
13 55 0025
13 55 0040
12 55 0000
12 55 0005
12 55 0015
12 55 0033
OU010
WATER
TEMP
CENT
19.9
19.6
18*. 2
17.3
16.7
29.2
28.1
27.3
24.8
22.7
00665
PHOS-TOT
MG/L P
0.033
0.027
0.020
0.021
0.021
0.024
0.025
U.025
0.031
0.0 94
U.022
0.02b
0.021
0.044
00300
DO
MG/L
9.8
7.0
4.8
3.8
7. 8
2.2
u.2
1.2
a.o
6. a
4.8
32217
CHLRPHYL
A
UG/L
7.0
8.5
7.0
00077 00094
TRANSP CNDUCTVY
SECCHI FIELD
INCHES M1CROMHO
54 170
165
175
160
165
50 186
181
189
189
219
46 203
197
198
255
11EPALES
3
00400 00410
PH
SU
8.20
8.30
7.90
7.60
7.60
8.60
8.50
7.90
7.60
7.40
7.80
7.70
7.60
7.40
T ALK
CAC03
MG/L
62
60
62
72
74
75
72
81
81
98
86
85
84
94
2111202
0049 FEET DEPTH
00610 00625 00630
NH3-N
TOTAL
MG/L
0.040
0.030
0.050
0.080
0.080
0.070
0.050
0.060
0.180
0.700
0.060
0.060
0.070
0.110
TOT
N
KJEL
MG/L
0
0
0
0
0
0
0
0
0
1
0
0
0
0
.600
.500
.400
.400
.400
.500
.300
.200
.300
.000
.300
.500
.200
.400
N02&N03
N-TOTAL
MG/L
0.410
0.400
0.490
0.540
0.560
0.050
0.050
0.070
0.320
0.160
0.080
0.080
0.080
0.100
00671
PHOS-DIS
ORTHO
MG/L P
0.003
0.002
0.002K
0.002K
0.002K
0.013
0.008
0.006
0.006
0.006
0.004
0.006
0.006
0.006
K VALUE KNOWN TO BE
LESS THAN INDICATED
-------
STORET RETRIEVAL DATE 75/01/27
210510
36 48 21.0 086 04 15.0
BARREN RIVER RESERVOIR
21009 KENTUCKY
DATE
FROM
TO
73/05/19
73/08/13
73/10/23
00010
TIME DEPTH WATER
OF TEMP
DAY FEET
13
13
13
13
13
14
14
14
14
13
13
13
13
50
50
50
50
50
20
20
20
20
15
15
15
15
0000
0004
0010
0015
0040
0000
0005
0015
0025
0000
0005
0015
.0028
CENT
19.8
19.7
19.2
17.9
16.5
28.3
28.6
26.3
23.7
29.5
29.5
29.6
29.6
00300 00077 00094
DO TRANSP CNDUCTVY
SECChI FIELD
MG/L INCHES MICHOMHO
54 165
6.4J 160
6.6 165
5.6 165
3.6 220
48 188
8.to 184
0.4 188
1.0 219
37 210
8.0 203
7.2 20t>
2.4 700
11EPALES
3
00400
PH
SU
8.00
7. 70
7.90
7.70
7.50
8.50
8.50
7.70
7.50
8.00
7.80
7.60
7.20
00*10
T ALK
CAC03
MG/L
70
70
71
69
74
77
73
79
97
do
85
86
133
211
0042
00610
NH3-N
TOTAL
MG/L
0.050
0.070
0.060
0.090
0.150
0.070
0.090
0.110
0.400
0.040
0.040
0.060
0.560
1202
FEET DEPTH
00625
TOT KJEL
N
MG/L
0.500
0.400
0.400
0.500
0.600
0.600
0.500
0.200
0.600
0.300
0.200K
0.200K
0.600
00630
N02iiN03
N-TOTAL
MG/L
0.410
0.510
0.460
0.560
0.580
0.050
0.110
0.250
0.280
0.030
0.040
0.060
0.490
00671
PHOS-OIS
ORTHO
MG/L P
0.002K
0.002K
0.002K
0.002K
0.004
0.006
0.007
0.006
0.007
0.005
0.006
0.007
0.008
00665 32217
DATE TIME DEPTH PHOS-TOT CHLRPHYL
FROM OF A
TO DAY FEET MG/L P UG/L
73/05/19 13 50 0000 0.021 3.1
13 50 0004 0.025
13 50 0010 0.023
13 50 0015 0.028
13 50 0040 0.0^7
73/08/13 14 20 0000 0.027 8.4
14 20 0005 0.02d
1<» 20 0015 0.027
It 20 0025 U.063
73/10/23 13 15 0000 0.032 10.t.
13 15 0005 0.026
13 15 0015 0.031
13 15 0028 0.035
LESS THAN INDICATED
K VALUE KNOWN TO BE
-------
SrORET RETRIEVAL DATE 75/01/27
210511
36 46 02.0 086 02 25.0
BARREN RIVER RESERVOIR
21009 KENTUCKY
11EPALES
3
2111202
0030 FEET
DEPTH
DATE
FROM
TO
73/05/19
73/08/13
73/10/23
TIME DEPTH
OF
DAY FEET
14 30 0000
14 30 0004
14 30 0015
14 30 0028
16 00 0000
16 00 0005
16 00 0010
13 35 0000
OU010
WATER
TEMP
CENT
19.1
19.0
18.3
16.8
30.1
27.6
26.6
29.3
00300 00077
DO TRANSP
SECCHI
MG/L INCHES
9.4
6.2
6.2
6.6
6.b
10.0
7
,P
II
S
36
30
14
00094
CNDUCTVY
FIELD
M1CROMHO
180
180
190
182
199
194
202
199
00400
PH
SU
7.80
7.90
7.60
7.70
8.20
8. lu
8.10
8.10
00410
T ALK
CAC03
MG/L
79
82
85
70
79
80
90
98
00610
NH3-N
TOTAL
MG/L
0.030
0.030
0.070
0.080
0.110
0.060
0.150
0.040
00625
TUT KJEL
N
MG/L
0.600
0.500
0.400
0.400
0.500
0.400
0.400
0.300
00630
N02&N03
N-TOTAL
MG/L
0.560
0.580
0.640
0.600
0.130
0.050
0.170
0.090
00671
PHOS-DIS
ORTHO
MG/L P
0.002
0.002K
0.002K
0.002K
0.007
0.006
0.007
0.006
DATE TIME DEPTH
FROM OF
TO DAY FEET
73/05/19 14 30 0000
14 30 0004
14 30 0015
14 30 0028
73/U8/13 16 00 0000
16 00 0005
16 00 0010
73/10/23 13 35 0000
0665
S-TOT
i/L P
0.028
0.027
0.020
0.026
0.059
0.042
0.047
0.058
32217
CHLRPHYL
A
UG/L
10.4
8.1
12.9
K VALUE KNOWN TO BE
LESS THAN INDICATED
-------
APPENDIX E
TRIBUTARY and WASTEWATER
TREATMENT PLANT DATA
-------
STORE! RETRIEVAL DATE 78/05/31
/TYPA/AMBNT/STREAM
DATE TIME DEPTH N02&N03
FROM OF N-
TO DAY FEET
73/04/13
73/05/01
73/06/17
73/07/22
73/08/19
73/09/16
73/10/14
73/11/17
74/01/20
74/01/30
74/02/13
74/02/28
74/03/29
11
12
09
08
08
11
07
11
09
12
08
13
12
30
45
25
15
55
10
30
45
05
25
33
00
50
2105A1 LS2105A1
37 01 30.0 085 59 30.0 4
BEAVER CREEK
21 7.5 GLASGOW N
I/BARREN RIVER RESVR 051691
BROG ON US 68 4 MI W OF GLASGOW
11EPALES
0000 FEET DEPTH CLASS 00
30
03
AL
L
1.5
1.5
2.0
1.4
1.4
0.8
0.3
0.4
1.7
1.5
1.4
1.4
1.4
00625
TOT KJEL
N
MG/L
0.180
0.1 OOK
0.630
0.690
0.100K
2.100
2.200
0.300
0.400
0.400
0.100K
2.200
0.400
00610
NH3-N
TOTAL
MG/L
0.042
0.007
0.078
0.044
0.020
0.072
0.294
0.016
0.040
0.035
0.005K
0.040
0.015
00671
PHOS-D1S
ORTHO
MG/L P
0.005K
0.010
0.017
0.030
0.012
0.021
0.011
0.012
0.020
0.015
0.015
0.005
00665
PHOS-TOT
MG/L P
0.025
0.030
0.080
0.130
0.055
0.045
0.045
0.012
0.040
0.030
0.015
0.030
0.030
K VALUE KNOWN TO BE
LESS THAN INDICATED
-------
STORE! RETRIEVAL DATE 78/05/31
/TYPA/AMBNT/STREAM
DATE TIME DEPTH N02&N03
FROM OF N-
TO DAY FEET
73/04/13
73/05/01
73/06/17
73/07/22
73/08/19
73/09/16
73/10/14
73/11/17
74/01/13
74/01/20
74/01/30
74/03/28
74/03/29
10 15
13 15
10 05
08 40
09 30
11 30
09 00
15 35
14 30
09 50
13 34
14 10
13 50
2105B1 LS2105B1
36 59 00.0 085 56 00.0 4
SOUTH FORK
21 7.5 GLASGOW S
T/BARREN RIVER RESVR
051691
BROG ON US 31E.1 MI S OF GLASGOW
11EPALES
0000 FEET DEPTH CLASS 00
>30
103
AL
L
1.4
1.2
1.4
1.5
0.8
0.3
1.0
0.2
1.4
1.7
1.7
1.3
1.3
00625
TOT KJEL
N
MG/L
0.210
0.200
0.210
0.500
2.310
1.760
1.050
0.400
0.100K
0.100
0.400
1.500
0.300
00610
NH3-N
TOTAL
MG/L
0.020
0.028
0.023
0.022
0.020
0.378
0.023
0.020
0.067
0.010
0.025
0.035
0.010
00671
PHOS-OIS
ORTHO
MG/L P
0.013
0.010
0.020
0.044
0.005K
0.015
0.036
0.010
0.025
0.020
0.010
0.020
00665
PHOS-TOT
MG/L P
0.025K
0.025
0.040
0.090
0.025
0.030
0.045
0.015
0.035
0.020
0.030
0.030
K VALUE KNOWN TO BE
LESS THAN INDICATED
-------
STORET RETRIEVAL DATE 78/05/31
/TYPA/AMBNT/STREAM
DATE TIME DEPTH N02&N03
FROM OF N-
TO DAY FEET MG/L
73/04/13
73/05/01
73/06/17
73/07/22
73/08/19
73/09/16
73/10/14
73/11/17
74/01/20
74/01/30
74/02/13
74/02/28
74/03/29
13
13
16
15
15
12
12
15
11
13
09
14
14
15
30
00
45
30
00
30
15
05
47
45
?5
00
2105B2
36 58 40.0 085 58 30.0 4
SOUTH FORK
21 7.5 GLASGOW S
T/8ARREN RIVER RESVR 051691
BANK 2.5 MI M OF GLASGOW
11EPALES
0000 FEET DEPTH CLASS 00
30
03
AL
L
1.0
1.0
1.7
1.8
0.3
0.2
0.2
0.2
1.4
1.3
1.2
1.2
1.3
00625
TOT KJEL
N
MG/L
4.100
3.990
4.800
2.700
7.600
11.000
6.750
9.000
1.100
4.000
2.000
3.700
3.300
00610
NH3-N
TOTAL
MG/L
1.790
2.000
3.000
1.200
4.300
5.700
0.087
4.300
0.300
1.050
0.760
1.150
1.570
00671
PHOS-DIS
ORTHO
MG/L P
0.660
0.830
1.800
0.840
3.700
4.300
2.200
3.700
0.490
0.750
0.630
0.540
0.600
00665
PHOS-TOT
MG/L P
1.000
1.150
1.930
0.995
4.200
4.650
2.500
4.300
0.630
0.930
0.890
0.870
0.930
-------
STORET RETRIEVAL DATE 78/05/31
/TYPA/ftMBNT/STREAM
DATE TIME DEPTH N02&N03
FROM OF IN
TO DAY FEET
73/04/13
73/05/01
73/06/17
73/07/22
73/08/19
73/09/16
73/10/14
73/11/17
74/01/20
74/01/30
74/02/13
74/02/28
74/03/29
10
13
09
08
09
11
07
11
09
12
08
13
13
35
00
00
30
10
25
50
25
20
45
45
22
10
2105C1 LS2105C1
36 59 30.0 085 57 00.0 4
MUGGINS BRANCH
21 7.5 GLASGOW S
T/8ARREN RIVER RESVR 051691
BRDG ON ST RT 1297 .2 MI W OF GLASGOW
11EPALES
0000 FEET DEPTH CLASS 00
630
N03
TAL
/L
o.e
0.7
0.4
0.9
0.2
0.1
0.2
0.03
1.1
0.9
0.9
0.8
0.7
00625
TOT KJEL
N
MG/L
0.210
0.390
0.405
0.260
1.900
3.100
0.700
0.600
1.800
0.400
1.350
1.500
0.400
00610
NH3-N
TOTAL
MG/L
0.042
0.099
0.054
0.037
0.044
0.170
0.086
0.020
0.040
0.015
0.055
0.085
0.025
00671
PHOS-DIS
ORTHO
MG/L P
0.005K
0.007
0.025
0.022
0.013
0.022
0.025
0.020
0.015
0.010
0.015
0.010
00665
PHOS-TOT
MG/L P
0.025
0.015
0.025
0.040
0.020
0.045
0.035
0.015
0.025
0.015
0.010
0.015
0.012
K VALUE IMMUWN TO HE
LESS THAN INDICATED
-------
STORE! RETRIEVAL DATE 78/05/31
/TYPA/AMBNT/STREAM
DATE TIME DEPTH N02&N03
FROM OF N-
TO DAY FEET
73/04/13
73/05/01
73/06/17
73/07/22
73/08/19
73/09/16
73/10/14
73/11/17
74/01/20
74/01/30
74/02/13
74/02/28
74/03/29
12 30
15 15
10 30
09 05
09 50
11 45
09 20
12 20
10 35
13 10
09 10
13 45
13 35
210SD1 LS2105D1
36 55 00.0 085 55 00oO 4
SKAGGS CREEK
21 7.5 GLASGOW S
T/BARREN RIVER RESVR
051691
8ROG ON HT 249 1.2 MI S OF BRISTLETOWN
11EPALES
0000 FEET DEPTH CLASS 00
30
03
AL
L
0.8
0.8
0.9
1.0
0.5
0.2
0.1
0.1
1.3
1.1
1.1
1.0
0.6
00625
TOT KJEL
N
MG/L
0.130
0.100K
0.440
0.260
1.980
2.200
0.850
0.300
0.500
0.100K
2.600
1.000
00610
NH3-N
TOTAL
MG/L
0.022
0.017
0.034
0.052
0.023
0.640
0.032
0.016
0.007
0.015
0.020
0.150
0.090
00671
PHOS-DIS
ORTHO
MG/L P
0.005K
0.005K
0.019
0.027
0.005K
0.010
0.010
0.012
0.010
0.015
0.010
0.010
00665
PHOS-TOT
MG/L P
0.025K
0.015
0.060
0.035
0.030
0.045
0.050
0.005
0.015
0.010
0.015
0.010
0.010
K VALUE KNOvJN TO 3£
LESS ThftN INDICATED
-------
STORE! RETRIEVAL DATE 78/05/31
/TYPA/AKBNT/STREAM
DATE TIME DEPTH N02S.N03
FROM OF iv
TO DAY FEET
73/03/31
73/04/28
73/06/11
73/07/22
73/08/19
73/09/16
73/10/15
73/11/28
73/12/27
74/01/26
74/02/23
74/03/31
10
17
11
09
09
14
12
14
16
11
14
16
05
no
30
00
00
30
35
35
15
25
15
25
2105E1 LS2105E1
36 45 30.0 086 02 00.0 4
GLOVER CREEK
21 7.5 AUSTIN
T/BARREN RIVER RESVR 051691
BRDG ON RD .5 MI SE BRUNS FORD BOAT RAMP
11EPALES
0000 FEET DEPTH CLASS 00
630
N03
TAL
/L
0.7
0.5
0.3
0.2
0.01
0.01
0.03
1.2
0.8
0.9
0.5
0.3
00625
TOT KJEL
N
MG/L
0.420
0.210
0.715
0.840
0.645
0.510
0.900
0.600
1.100
0.100K
0.600
0.200
00610
NH3-N
TOTAL
MG/L
0.168
0.010
0.078
0.050
0.039
0.042
0.042
0.016
0.016
0.020
0.030
0.020
00671
PHOS-DIS
ORTHO
MG/L P
0.005K
0.005K
0.008
0.026
0.015
0.009
0.010
0.048
0.020
0.010
0.005
0.010
00665
PHOS-TOT
MG/L P
0.020
0.020
0.045
0.085
0.045
0.045
0.045
0.020
0.020
0.030
0.010
K VALUE K'MU*^ Tu t)£
LESS TH*N INDICATED
-------
STORET RETRIEVAL DATE 78/05/31
/TYPA/AMBNT/STREAM
DATE TIME DEPTH N02&N03
FROM OF f>
TO DAY FEET
73/03/31
73/04/28
73/06/11
73/07/22
73/08/19
73/09/16
73/10/15
73/11/28
73/12/27
74/01/26
74/02/23
74/03/31
10
17
11
09
09
14
17
14
16
11
14
16
15
10
45
00
05
35
45
38
00
15
45
00
2105F1 LS2105F1
36 45 30.0 086 02 00.0 4
TRACE CREEK
21 7.5 AUSTIN
T/BARREN RIVER RESVR
051691
8RDG ON RD .25 MI NE BRWN FORD BOAT RAMP
11EPALES
0000 FEET DEPTH CLASS 00
630
N03
TAL
/L
o.e
0.5
0.3
0.2
0.01K
0.01K
0.05
0.9
0.8
0.9
0.9
0.9
00625
TOT KJEL
N
M6/L
0.255
0.700
0.480
0.840
1.680
0.4BO
0.850
0.800
0.300
0.200
1.300
0.200
00610
NH3-N
•TOTAL
MG/L
0.026
0.160
0.069
0.029
0.035
0.031
0.130
0.020
0.016
0.065
0.030
0.020
00671
PHOS-DIS
OP.THO
MG/L P
0.005K
O.OOSK
0.007
0.023
0.009
0.008
0.013
0.044
0.016
0.015
0.010
0.005
00665
PHOS-TOT
MG/L P
0.020
0.030
0.035
0.080
0.035
0.040
0.035
0.020
0.020
0.020
0.005
K VALUE KiNOdN 10 BE
LESS THAN INDICATED
-------
STORET RETRIEVAL DATE 78/05/31
/TYPA/AMBNT/STREAM
DATE TIME DEPTH N02&N03
FROM OF f
TO DAY FEET
73/03/31
73/04/28
73/07/22
73/08/19
73/09/16
73/10/15
73/11/28
73/12/27
74/01/26
74/02/23
74/03/31
10
17
09
09
14
18
15
16
11-
14
15
30
15
10
15
40
00
no
20
00
30
50
310561 LS2105G1
36 45 30.0 086 02 30.0 4
RriODEN CREEK
21 7.5 AUSTIN
T/BARREN RIVER RESVH
051691
BRDG ON ST RT 98 2 MI ESE OF MAYNARD
11EPALES
0000 FEET DEPTH CLASS 00
630
N03
TAL
/L
0.6
0.3
0.2
0.01K
0.01K
0.01K
1.3
0.8
0.8
0.7
0.5
00625
TOT KJEL
N
MG/L
0.200
0.380
0.705
1.260
0.880
2.000
0.100
0.200
0.300
0.500
0.200
00610
NH3-N
TOTAL
MG/L
0.018
0.021
0.029
0.044
0.160
0.132
0.008
0.010
0.045
0.040
0.010
00671
PHOS-DIS
ORTHO
MG/L P
0.005K
0.005K
0.023
0.010
0.008
0.012
0.012
0.012
0.010
0.010
0.005K
00665
PHOS-TOT
MG/L P
0.015
0.020
0.075
0.040
0.037
0.040
0.050
0.012
0.020
0.015
0.012
K VALUE K.MO*N ru BE
LESS TH^N INDICATED
-------
STOHET RETRIEVAL DATE 78/05/31
/TYPA/AMBNT/STREAM
DATE TIME DEPTH N02&N03
FROM OF N-
TO DAY FEET
73/03/31
73/04/28
73/07/22
73/08/19
73/09/16
73/10/15
73/11/28
73/12/27
74/01/26
74/02/23
74/03/31
10
17
09
09
15
17
13
16
10
11
15
16.
50
30
40
35
00
30
00
25
45
10
00
30
2105H1 LS2105H1
36 42 30.0 085 05 00.0 4
LONG CREEK
21 7.5 HOLLAND
T/BARRE RIVER RESVR
052091
8RDG ON ST RT 100 1.2 MI NWOF HOLLAND
11EPALES
0000 FEET DEPTH CLASS 00
• 30
103
AL
L
0.8
0.7
0.6
0.4
0.4
0.2
1.2
1.2
0.9
0.8
0.8
0.7
00625
TOT KJEL
N
M6/L
0.140
0.150
0.120
1.890
0.840
1.780
0.500
0.700
0.300
0.700
1.700
0.100
00610
NH3-N
TOTAL
MG/L
0.005K
0.021
0.021
0.047
0.252
0.113
0.008
0.020
0.025
0.025
0.060
0.020
00671
PHOS-OIS
ORTHO
MG/L P
0.006
0.005K
0.016
0.011
0.008
0.011
0.024
0.012
0.010
0.025
0.010
0.005K
00665
PHOS-TOT
MG/L P
0.015
0.015
0.025
0.025
0.025
0.027
0.020
0.020
0.063
0.022
0.010
K VALUE K.'JCHN TO 6E
LESS THAN INDICATED
-------
STORET RETRIEVAL DATE 78/05/31
/TYPA/AM6NT/STREAM
DATE TIME DEPTH N02&N03
FROM OF N-
TO DAY FEET MG/L
73/03/31
73/04/28
73/07/22
73/08/19
73/09/16
73/10/15
73/11/28
73/12/27
74/02/23
74/03/31
11 05
17 45
09 20
09 45
15 05
17 55
16 30
16 30
15 15
16 40
2io5Ji LS2105J1
36 42 00.0 086 03 00.0 4
BARREN RIVER
21 7.5 HOLLAND
I/BARREN RIVER RESVR 051691
6POG ON ST HT 100 1.5 MI E OF HOLLAND
11EPALES
0000 FEET DEPTH CLASS 00
30
03
AL
L
0.7
0.5
0.7
0.1
0.3
0.1
0.9
1.2
0.8
0.6
00625
TOT KJEL
N
MG/L
0.210
0.290
0.800
1.050
0.620
1.600
2.200
0.200
1.600
0.300
00610
NH3-N
TOTAL
MG/L
0.023
0.063
0.037
0.058
0.024
0.115
0.104
0.012
0.030
0.025
00671
PHOS-DIS
ORTHO
MG/L P
0.010
0.010
0.029
0.013
0.008
0.010
0.044
0.020
0.015
0.010
00665
PHOS-TOT
MG/L P
0.030
0.030
0.070
0.050
0.045
0.045
0.032
0.040
0.030
-------
STORET RETRIEVAL DATE 78/05/31
/TYPA/AMBNT/STREAM
DATE TIME DEPTH N02&.N03
FROM OF l\
TO DAY FEET
73/04/13
73/05/01
73/06/17
73/07/22
73/08/19
73/09/16
73/10/15
73/11/28
74/01/20
74/01/30
74/02/13
74/02/28
74/03/29
09
14
13
11
12
13
15
10
14
14
10
14
14
00
10
35
05
25
40
00
40
45
18
10
50
45
2105J2
36 S3 50.0 086 08 05.0 4
BARREN RIVER
21 7.5 MEADOR
0/BAHREN RIVER RESVR 051691
BANK AT GAGING STA BELO BARREN RIVER DAM
11EPALES
0000 FEET DEPTH CLASS 00
630
NO 3
TAL
/L
0.8
0.8
0.6
0.2
0.02
0.03
0.04
0.3
1.0
0.9
1.0
1.0
0.8
00625
TOT KJEL
N
MG/L
0.240
0.230
0.310
0.600
1.600
1.260
1.050
0.400
0.400
0.500
0.300
0.500
00610
NH3-N
TOTAL
MG/L
0.023
0.044
0.058
0.220
0.067
0.290
0.730
0.012
0.105
0.040
0.035
0.035
0.120
00671
PHOS-DIS
ORTHO
MG/L P
0.005K
0.007
0.005K
0.010
0.005K
0.005K
0.009
0.005K
0.030
0.030
0.030
0.010
0.010
00665
PHOS-TOT
MG/L P
0.02SK
0.025
0.015
0.020
0.020
0.020
0.030
0.065
0.070
0.065
0.055
0.045
0.065
K VALUE KNOWN TO Bt
LESS THAN INDICATED
-------
STORcT RETRIEVAL DATtL 75/02/03
2105BA TF2105BA P010070*
36 59 00.0 085 57 50.0
GLAbGOW
21 7.5 GLASGOW 50UT
T/bAR«EN LAKE
b FORK BEAVER CREEr>
11EPALES 2141204
4 0000 FEET DEPTH
DATE
FROM
TO
73/04/17
CPU1-
73/04/18
7J/05/06
CPU1-
73/05/08
73/06/14
CP(T)-
73/06/ 16
73/U8/ 14
Cf (T)-
73/08/16
7 j/09/ 19
73/10/02
C^(T>-
73/10/03
73/11/05
CP-
73/11/06
73/12/04
CP(T)-
7j/12/0b
74/01/21
74/02/06
74/03/30
00630
TIME DEPTH N02\N03
OF N-TOTAL
DAY FEET MG/L
08
08
00
24
07
07
OH
08
UU
U7
07
07
07
08
08
09
U9
00
00
GO
00
30
30
30
30
00
00
00
00
00
00
00
00
00
0
0
w
0
0
0
0
1
1
1
.130
.375
.270
.110
. IbU
.040
.310
. bciO
.400
.240
00625
TOT KJfL
N
MG/L
22.000
13.300
21.000
22.000
17.360
34.800
31.500
2«.uOO
10.000
7.100
l.OOOK
00610 00671
NH3-N PnOS-OIS
TOTAL ORTHO
MG/L MG/L P
4
1
4
1
3
10
8
2
0
0
0
.700
.58U
.000
.9du
.700
.500
.000
.400
.250
.560
.260
5.o50
4.300
7.000
2.bOO
7.600
8.000
7.525
•3.SOO
2.000
2.900
1.300
00665 50051 50053
PHOS-TOT FLO* CONuuIT
RATE FLOjv-MGO
MG/L P INST MGO MONTHLY
7.800
6.100
'i.aOd
5.740
8.95o
11.300
12.000
8.500
2.400
3.700
2.100
2.100
3.300
2.200
2.800
1.900
1.800
l.bOO
4.000
3.SOO
4.200
6.000
2.400
2.800
2.780
2.500
1.W30
1.600
1.700
2.000
4.000
6.100
4.000
-------
STORET KETRIEVAL DATE 75/02/03
DATE
FROM
TO
73/06/21
CP(T>-
73/06/21
73/08/07
CP(T)-
73/08/07
73/09/11
CP(T>-
73/09/11
74/02/07
7<*/02/07
74/03/OH
CP(T>-
74/03/08
74/04/11
CPUJ-
74/04/11
74/U5/13
CP(T>-
7«*/05/ 13
74/06/14
CP(T)-
74/o6/ 1<*
74/o7/ Ib
CP(T)-
7<*/07/16
74/OB/18
74/09/24
CP(T)-
74/09/2"*
74/10/29
CP(T)-
74/10/29
00630 00625
TIME DEPTH N02MM03 TOT KJEL
OF N-TOTAL N
DAY FEET MG/L MG/L
00 00
6.000 2.400
12 00
07 00
0.300 8.100
15 00
00 00
6.400 0.760
24 00
11 00
1.120 1.700
16 00
11
Ib
11
16
11
16
11
Ib
11
16
11
11
16
11
16
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
u.
7.
0.
1.
0.
0.
3.
1U.
240
400
360
76o
6<*0
3bO
780
«0d
2
1
1
1
2
1
1
2
.500
.OOOK
.800
.OOOK
.700
.900
.550
.450
210521 AS210521 P002207
36 42 25.0 085 41 30.0
TOMPKINSVILLE
21009 250 COR8IN
T/riAKREN KESErfvOlK
MILL CKEEK / BARREN RIVER
11EPALES 2141204
4 0000 FEET DEPTH
00610 00671 00665 50051 50053
NH3-N PrlOS-DIS PHOS-TOT FLOW CONDUIT
TOTAL O^THO KATE FLOW-MGO
MG/L MG/L P MG/L P INST MGD MONTHLY
0.250 9.100 9.200 O.lo7
0.250
0.210
0.071
4.900
b.450
7.350
0.085 7.400
0.050K 9.8UO
0.100 7.200
O.llo 6.850
d.500
9.HOO
10.500
8. 150
0.250 0.205
0.273 13.900 14.000 0.306 0.275
0.324 0.258
0.050 5.750 6.100 0.260 0.230
0.130 5.400 s>.600 0.300 0.260
O.OSuK 8.000 8.700 0.270 0.260
0.250
0.290
0.240
0.350
0.260
0.230
0.222
0.280
0.324 0.4&0
------- |