U.S. ENVIRONMENTAL PROTECTION AGENCY
NATIONAL EUTROPHICATION SURVEY
WORKING PAPER SERIES
REPORT
ON
LAKE MURRAY
FAIRFIELD, LEXINGTON, NEWBERRY,
SALUDA, AND RICHLAND COUNTIES
SOUTH CAROLINA
EPA REGION IV
WORKING PAPER No, 436
CORVALLIS ENVIRONMENTAL RESEARCH LABORATORY - CORVALLIS, OREGON
and
ENVIRONMENTAL MONITORING & SUPPORT LABORATORY - LAS VEGAS, NEVADA
T^G.P.O. 699-440
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REPORT
ON
LAI^WRRAY
FAIRFIELD, LEXINGTON, NEWBERRY,
SALUDA, AND RICHLAND COUNTIES
SOUTH CAROLINA
EPA REGION IV
WORKING PAPER No,
WlTH THE COOPERATION OF THE
SOUTH CAROLINA DEPARTMENT OF HEALTH AND
ENVIRONMENTAL CONTROL
AND THE
SOUTH CAROLINA NATIONAL GUARD
JUNE, 1975
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CONTENTS
Page
Foreword i i
List of South Carolina Study Lakes iv
Lake and Drainage Area Map v
Sections
I. Conclusions 1
II. Lake and Drainage Basin Characteristics 5
III. Lake Water Quality Summary 6
IV. Nutrient Loadings 12
V. Literature Reviewed 21
VI. Appendices 22
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FOREWORD
The National Eutrophication Survey was initiated in 1972 in
response to an Administration commitment to investigate the nation-
wide threat of accelerated eutrophication to 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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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
freshwater lakes. Likewise, multivariate evaluations for the
relationships between land use, nutrient export, and trophic
condition, by lake class or use, are being developed to assist
in the formulation of planning guidelines and policies by EPA
and to augment plans implementation by the states.
ACKNOWLEDGMENT
The staff of the National Eutrophication Survey (Office of
Research & Development, I). S. Environmental Protection Agency)
expresses sincere appreciation to the South Carolina Department
of Health and Environmental Control for professional involvement,
to the South Carolina National Guard for conducting the tributary
sampling phase of the Survey, and to those South Carolina waste-
water treatment plant operators who voluntarily provided effluent
samples and flow data.
The staff of the South Carolina Bureau of Wastewater and
Stream Quality Control provided invaluable lake documentation
and counsel during the Survey, reviewed the preliminary reports,
and provided critiques most useful in the preparation of this
Working Paper series.
Major General Robert L. McCrady, the Adjutant General of South
Carolina, and Project Officer Lt. Colonel John P. DuPre (Retired),
who directed the volunteer efforts of the South Carolina National
Guardsmen, are also gratefully acknowledged for their assistance
to the Survey.
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IV
NATIONAL EUTROPHICATION SURVEY
STUDY LAKES
STATE OF SOUTH CAROLINA
NAME
Clark Hill
Fishing Creek
Greenwood
Hartwel 1
Keowee
Marion
Moultrie
Murray
Robinson
Saluda
Secession
Wateree
William C. Bowen
Wylie
COUNTY
Abbeville, McCor-
mick, SC; Colum-
bia, Elbert, Lin-
coln, McDuffie,
Wilks, GA
Chester, Lancaster
Greenwood, Laurens,
Newberry
Anderson, Oconee,
Pickens, SC;
Franklin, Hart,
Stephens, GA
Oconee, Pickens
Berkeley, Calhoun,
Claredon, Orange-
burg, Sumter
Berkeley
Lexington, Newberry,
Rich!and, Saluda
Chesterfield, Dar-
lington
Greenville, Pickens
Abbeville, Anderson
Fairfield, Kershaw,
Lancaster
Spartanburg
York, SC; Gaston,
Mecklenburg, NC
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MAP LOCATION
Greenwoo
South Greenwood
LAKE MURRAY
Tributary Sampling Site
X Lake Sampling Site
* Sewage Treatment Facility
J5 Direct Drainage Area Boundary
o 10
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LAKE MURRAY
STORE! NO. 4507
I. CONCLUSIONS
A. Trophic Condition:
Collectively, the Survey data indicate Lake Murray is eutro-
phic. However, Lake Murray is a large reservoir and when the
data are examined on a station-by-station basis, mesotrophy is
indicated at stations 1, 2, and 7; meso-eutrophy is indicated at
station 3; and eutrophy is indicated at stations 4, 5, and 6
(see map, page v). Following is a tabulation of the means of
six relevant parameters for each of the sampling stations:
OP TP Inorg. N TN Secchi Chlor. a
Station (mg/1) (mg/1) (mg/1) (mg/1) disc (m) (ug/1)
1
2
7
3
4
5
6
0.007
0.007
0.007
0.010
0.013
0.015
0.014
0.020
0.019
0.017
0.023
0.040
0.048
0.057
0.251
0.257
0.244
0.264
0.326
0.319
0.302
0.505
0.540
0.530
0.529
0.716
0.654
0.692
2.4
2.4
2.4
2.1
1.7
1.4
0.9
5.3
5.5
6.0
6.2
6.8
7.9
7.4
Lake Murray ranked sixth in overall trophic quality when the
13 South Carolina lakes sampled in 1973 were compared using a
combination of six water quality parameters*. Four of the lakes
had less median total phosphorus, six had less and one had the
same median dissolved phosphorus, four had less and one had the
same median inorganic nitrogen, six had less mean chlorophyll a_,
and two had a greater mean Secchi disc transparency. Depression
* See Appendix A.
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2
or depletion of dissolved oxygen with depth occurred at all sam-
pling stations in July and September.
Blue-green algae were prominent in the July and September
phytoplankton samples, but surface concentrations of algae were
not observed by Survey limnologists.
B. Rate-Limiting Nutrient:
The algal assay results indicate Lake Murray was phosphorus
limited at the time the sample was collected (09/22/73). The
lake data indicate phosphorus limitation at all sampling times.
C. Nutrient Controllability:
1. Point sources—The estimated phosphorus contribution
of point sources accounted for 60.0% of the total phosphorus
load reaching Lake Murray during the sampling year. The largest
part of the point-source load (26.3%) came from the City of Green-
ville and 12 smaller municipal wastewater treatment facilities
which discharge in the drainage of upstream Lake Greenwood (a
portion of the phosphorus contributed by these plants reaches
Lake Murray via the Lake Greenwood outlet and the Saluda River).
The second largest phosphorus contributor was the City of
Greenwood in the Lake Murray drainage (12.3% of the total). The
four Newberry plants collectively contributed 8.6% of the total
phosphorus load, and the remaining 12.7% was input to Lake Murray
by ten smaller wastewater treatment facilities.
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3
No accounting was made of those industrial wastes which are
not treated in municipal treatment facilities, and the estimated
phosphorus load contributed by the City of Greenwood was not
adjusted to account for the significant industrial load treated
in the municipal plant (Foley, 1976). Therefore, it is very
likely that more than 60.0% of the total phosphorus load to Lake
Murray was input by point sources.
The phosphorus loading measured during the sampling year,
1.45 g/m2, is about twice that proposed by Vollenweider (Vollen-
weider and Dillon, 1974) as a eutrophic loading (see page 20).
It is calculated that 85% phosphorus removal at the point sources
identified in this report would result in a phosphorus loading to
Lake Murray of 0.71 g/m2/yr. While the reduced phosphorus loading
would be slightly more than the eutrophic loading of 0.70 g/m2/year,
it is likely that such a reduction would result in significant
improvement in the Saluda River embayment where water quality
currently is poorest (stations 4, 5, and 6) as well as reduce the
phosphorus load discharged through the outlet to downstream Lake
Marion*.
2. Non-point sources—The non-point phosphorus load to Lake
Murray amounted to 40.0% of the total load. For the reasons
noted above, this probably is an overestimate of the non-point
source contribution because of industrial contributions and under-
* Working Paper No. 434.
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4
estimation of contributions of some of the municipal sources.
Note that the phosphorus export rates of the Little Saluda
River, Big Creek, and the Bush River were much higher than the
rates of the other tributaries of Lake Murray (see page 19).
These rates indicate probable point-source impact.
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II. LAKE AND DRAINAGE BASIN CHARACTERISTICS1"
A. Lake Morphometry :
1. Surface area: 205.58 kilometers2.
2. Mean depth: 12.7 meters.
3. Maximum depth: 57.8 meters.
4. Volume: 2,608 x 106 m3.
5. Mean hydraulic retention time: 348 days.
B. Tributary and Outlet:
(See Appendix C for flow data)
1. Tributaries -
Drainage Mean flow
Name area (km2)* (m3/sec)*
Saluda River 4,325.3 61.82
Horse Creek 20.4 0.29
Hollow Creek 44.8 0.63
Clouds Creek 238.8 3.39
Richland Creek 49.7 0.71
Little Saluda River 284.1 4.03,
Big Creek 127.4 1.81
Indian Creek 24.0 0.34
Bush River 303.0 4.28
Minor tributaries &
immediate drainage - 644.9 9.36
Totals 6,062.4 ' 86.66
2. Outlet -
Saluda River 6,268.0** 86.66
C. Precipitation***:
1. Year of sampling: 173.9 centimeters.
2. Mean annual: 120.0 centimeters.
t Table of metric conversions—Appendix B.
tt At maximum controllable pool level; Martin and Hanson, 1966.
* For limits of accuracy, see Working Paper No. 175, "...Survey Methods,
1973-1976".
** Includes area of lake.
*** See Working Paper No. 175.
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6
III. LAKE WATER QUALITY SUMMARY
Lake Murray 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 a number of depths at seven stations
on the lake (see map, page v). During each visit, a single depth-
integrated (4.6 m to surface) sample was composited from the stations
for phytoplankton identification and enumeration; and during the
last visit, two 18.9-liter depth-integrated algal assay samples
were composited (stations 1, 2, and 3, were combined; and stations
4, 5, and 6 were combined). Also each time, a depth-integrated
sample was collected from each of the stations for chlorophyll
a_ analysis. The maximum depths sampled were 54.6 meters at station
1, 41.5 meters at station 2, 39.6 meters at station 3, 32.3 meters
at station 4, 17.1 meters at station 5, 9.1 meters at station 6,
and 26.2 meters at station 7.
The results obtained are presented in full in Appendix D and
are summarized in the following table.
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PARAMETER
TEMP (C)
DISS 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 ( 3/26/73)
7 SITES
RANGE MEAN MEDIAN
9.3 - 15.3 12.4 12.6
7.6 - 10.4 9.4 9.6
58. - 78. 66. 65.
7.2 - 7.9 7.5 7.5
10. - 19. 14. 15.
0.018 - 0.093 0.037 0.028
0.003 - 0.023 0.009 0.007
0.180 - 0.390 0.257 0.250
0.010 - 0.080 0.038 0.030
0.200 - O.ROO 0.315 0.300
0.210 - 0.430 0.295 0.280
0.380 - 1.140 0.571 0.525
4.8 - 8.4 5.7 5.0
0.5 - 1.8 1.3 1.4
CHEMICAL CHARACTERISTICS FOR LAKE MURRAY
STORET COOE 4507
2ND SAMPLING ( 7/ 9/73)
7 SITES
RANGt
14.4
0.3
55.
6.2
14.
0.007
0.003
0.040
0.050
0.200
0.090
0.250
4.4
1.2
- 31.1
8.6
75.
8.4
25.
- 0.092
- 0.026
- 0.440
- 0.400
- 1.000
- 0.520
- 1.270
9.7
2.7
Mb AN
?3.4
3.7
64.
6.9
19.
0.023
0.007
0.207
0.101
0.427
0.308
0.633
7.1
2.2
MEDIAN
24.0
3.1
63.
6.4
19.
0.015
0.005
0.180
0.070
0.400
0.340
0.590
7.4
2.4
3RD SAMPLING ( 9/32/73)
7 SITES
RANGE MEAN MEDIAN
17.6 - 28.0 24.4 25.7
0.0 - 9.0 2.9 1.5
48. - 102. 58. 56.
6.2 - 8.3 6.5 6.5
17. - 30. ,23. 22.
0.010 - 0.073 0.027 0.020
0.004 - 0.050 0.013 0.010
0.020 - 0.190 0.043 0.030
0.030 - 0.660 0.173 0.110
0.200 - 1.200 0.517 0.400
0.050 - 0.690 0.210 0.150
0.230 - 1.230 0.560 0.490
4.8 - 10.1 6.5 5.4
1.0 - 3.0 2.3 2.6
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B. Biological Characteristics:
1. Phytoplankton -
Sampling
Date
03/26/73
07/09/73
09/22/73
2. Chlorophyll a_ -
Sampling
Date
03/26/73
Dominant
Genera
1.
2.
3.
4.
5.
1.
2.
3.
4.
5.
6.
1.
2.
3.
4.
5.
Melosira sp.
Flagellates
Cryptomonas sp.
Fragilaria sp.
Stephanodiscus sp.
Other genera
Total
Nitzschia sp.
Anabaena s p.
Cyclotella sg_,
Lyngbya sp.
Synedra sp.
Other genera
Total
Dactylococcopsis sp.
Raphidiopsis sp.
Lyngbya S£.
Anabaena sp.
Chroococcus sp.
Other genera
Total
Algal Units
per ml
669
669
278
138
106
351
2,211
2,429
1,404
1,350
1,026
756
4,263
11,228
Station
Number
1
2
3
4
5
6
7
5,110
Chlorophyll a_
(yg/D
4.8
4.9
5.9.
4.9
6.2
8.4
5.0
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Sampling
Date
07/09/73
09/22/73
Station
Number
1
2
3
4
5
6
7
1
2
3
4
5
6
7
C. Limiting Nutrient Study:
1. Stations 1, 2, 3 -
a. Autoclaved, filtered, and nutrient spiked
Spike (mg/1)
Ortho P
Cone, (mg/lj
Inorganic N
Cone, (mg/ll
Control 0.009
0.010 P 0.019
0.020 P 0.029
0.050 P 0.059
0.025 P + 0.5 N 0.034
0.050 P + 1.0 N 0.059
1.0 N 0.009
b. Filtered and nutrient spiked -
0.246
0.246
0.246
0.246
0.746
1.246
1.246
Spike (mg/1)
Control
0.010 P
0.020 P
0.050 P
0.025 P + 0.5 N
0.050 P + 1
1.0 N
0 N
Ortho P
Cone, (mg/1)
0.007
0.017
0.027
0.057
0.032
0.057
0.007
Inorganic N
Cone, (mg/1)
0.232
0.232
0.232
0.232
0.732
1.232
1.232
Chlorophyll a
(yg/1)
6.0
6.7
7.4
9.7
7.5
4.4
8.1
5.0
4.8
5.4
5.9
10.1
9.3
5.0
Maximum yield
(mg/l-dry wt.)
0.3
4.6
7.7
7.6
11.9
24.6
0.2
Maximum yield
(mg/l-dry wt.}
0.3
3.8
5.7
6.4
11.0
24.6
0.3
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10
Stations 4, 5, 6 -
a. Autoclaved, filtered, and nutrient spiked -
Spike (mg/1)
Ortho P
Cone, (mg/1)
Inorganic N
Cone, (mg/1)
Maximum yield
(mg/1-dry wt.)
Control
0.010 P
0.020 P
0.050 P
0.025 P + 0.5 N
0.050 P + 1.0 N
1.0 N
0.019
0.029
0.039
0.069
0.044
0.069
0.019
b. Filtered and nutrient spi
Spike (mg/1)
Control
0.010 P
0.020 P
0.050 P
0.025 P + 0.5 N
0.050 P + 1.0 N
1.0 N
Discussion -
The control
Ortho P
Cone, (mg/1)
0.016
0.026
0.036
0.066
0.041
0.066
0.016
yields of the
0.384
0.384
0.384
0.384
0.884
1.384
1.384
ked -
Inorganic N
Cone, (mg/1)
0.375
0.375
0.375
0.375
0.875
1.375
1.375
6.6
9.5
11.5
13.0
20.6
34.5
7.4
Maximum yield
(mg/1 -dry wt.)
7.2
9.7
7.9
10.3
19.6
32.0
7.0
assay alga, Selenastrum capri-
cornutum, indicate that the potential primary
productivity
at stations 1, 2, and 3 was moderate but was high at stations
4, 5, and 6 at the time the assay samples were collected (09/
22/73). In both assays, increasing yields with increasing
increments of orthophosphorus indicate that Lake Murray was
limited by phosphorus at that time. Note that in all cases,
the addition of nitrogen alone did not produce a yield sig-
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n
nificantly greater than that of the control.
The differences in the control yields at stations 1,
2, and 3 (east end of lake) and at stations 4, 5, and 6
(west end of the lake) indicate the differences in avail-
ability of nutrients for primary production. Note that
orthophosphorus concentrations at stations 1, 2, and 3 were
about one-half those at stations 4, 5, and 6.
The lake data also indicate Lake Murray was phosphorus
limited. At all sampling times, the mean inorganic nitrogen
to orthophosphorus ratios .were 17 to 1 or greater.
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12
IV. NUTRIENT LOADINGS
(See Appendix E for data)
For the determination of nutrient loadings, the South Carolina
National Guard collected monthly near-surface grab samples from each
of the tributary sites indicated on the map (page v), except for the
high runoff month of January when two samples were collected. Sampling
was begun in February, 1973, and was completed in February, 1974.
Through an interagency agreement, stream flow estimates for the
year of sampling and a "normalized" or average year were provided by
the South Carolina District Office of the U.S. Geological Survey for the
tributary sites nearest the lake.
Except for the Little Saluda River, nutrient loads for sampled
tributaries were determined by using a modification of a U.S. Geological
Survey computer program for calculating stream loadings*. Stream
loads shown are those measured minus point-source loads, if any.
Nutrient loads for the Little Saluda River were calculated using
the mean annual flow and adjusted mean phosphorus and nitrogen con-
centrations at station F-l. Abnormally high levels of phosphorus and
nitrogen were recorded for the October, November, and December samples
which resulted in excessive loading values. The loads reported herein
are based on values excluding the apparent outliers.
Nutrient loads for unsampled "minor tributaries and immediate
drainage" ("II" of U.S.G.S.) were estimated using the nutrient loads
* See Working Paper No. 175.
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13
at station B-l, in kg/km2/year, and multiplying by the ZZ area in km2.
The indirect municipal point-source loads leaving upstream Lake
Greenwood* were calculated by multiplying the nutrient loads leaving Lake
Greenwood (90,815 kg P and 1,448,195 kg N) by the fractions of the totals
of the nutrient loads contributed by the 13 listed point sources (0.862
for P and 0.399 for N).
The operators of the Batesburg, Newberry (Ocona, Boundary Street,
Gum Springs, and Pool No. 1), Prosperity No. 1 and No. 2, and Saluda
wastewater treatment plants provided monthly effluent samples and cor-
responding flow data. The operators of the Clinton, Greenwood, Joanna
Mills Village, Laurens,, Leesville, Ninety Six, and Ridge Springs waste-
water treatment plants did not participate in the Survey, and nutrient
loads were estimated at 1.134 kg P and 3.401 kg N/capita/year.
* Working Paper No. 431.
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14
A. Waste Sources:
1. Known municipal
Name
Batesburg
Clinton
Greenwood
Joanna Mills
Village
Laurens
Leesville
Newberry
Ocona (#2)
Boundary St.
Gum Springs
Pool #1
Ninety Six
Prosperity
#1 - S,W.
#2 - N.W.
Ridge Spring #2
Saluda
Pop.
Served
4,385
7,900
35,000
1,830
9,600
800
400
10,000
160
1,500
2,400
100
300
500
2,500
Mean Flow
Treatment Cm
tr. filter
2 stab, ponds
act. sludge 1
act. sludge
tr. filter
stab, pond
act. sludge
tr. filter
stab, pond
stab, pond
stab, pond
aer. pond
aer. pond
stab, pond
tr. filter +
3/d)
950.0
2,422.4
1,355.0
556.4
3,633.6*
473.1
1,922,8
4,349.0
11.4
567,8
908.4
109.8
151.4
189.2*
1,347.5
Receiving
Water
West Cfeek
Bush Riyer
Wilson Creek
Bush River
Little River
Clouds Creek
Gum Spring Creek/
Bush River
Scott Creek/
Bush River
Gum Spring Creek
Bush Creek/
Bush River
Br. of Ninety
Six Creek
Timothy Creek
Timothy Creek
Clouds Creek
Little Saluda River
pond
In addition to the sources listed above, at least eleven
privately-owned facilities treating domestic wastes (combined
flow of 880 m3/day) discharge in the Lake Murray drainage (Foley,
1976); the nutrient impact of these small sources is not known
but probably is minimal.
2. Lake Greenwood municipal -
The following sources discharge in the Lake Greenwood drainage,
and a portion of the nutrient loads reaches Lake Murray via the
Saluda River.
t Survey questionnaires; Anonymous, 1971; Foley, op. cit-
* Estimated at 0.3785 m3/capita/day.
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Name
Belton
Easley
Georges Creek
Glenwood
Brushy Creek
Greenville
Honea Path
#1
#2
Piedmont
Ware Shoals
#1
#2
West Pelzer
Williams ton
#1
#2
Pop.
Served
1,200
2,800
2,000
3,000
115,000
4,000
2,000
1,405
1,600
1,200
1,000
1,300
2,500
15
Treatment
stab, pond
stab, pond
stab, pond
stab, pond
tr. filter
stab, pond
stab, pond
act. sludge
stab, pond
act. sludge
act. sludge
stab, pond
act. sludge
Mean Flow
(m3/d)
836.5
1,059.8
757.0
1,135.5
98,569.0
927.3
757.0
757.0
832.7
17,513.2
295.2
283.9
1,419.4
Receiving
Water
Broad Mouth Cr.
Georges Creek/
Saluda River
Br. of Brushy
Creek
Brushy Creek/
Saluda River
Reedy River
Broad Mouth Creek
Clatworthy Creek/
Saluda River
Grove Creek/
Saluda River
Turkey Creek
Saluda River
Saluda River
Saluda River
Big Creek
3. Known industrial -
At least eight industrial treatment facilities with a combined
design flow about 3,320 m3/day discharge in the Lake Murray drainage
(Foley, op. cit.), but the nutrient significance of these sources is
not known.
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16
B. Annual Total Phosphorus Loading - Average Year:
1. Inputs -
kg P/ % of
Source yr total
a. Tributaries (non-point load) -
Saluda River 38,330 12.9
Horse Creek 350 0.1
Hollow Creek 1,295 0.4
Clouds Creek 8,305 2^8
Richland Creek 1,295 0.4
Little Saluda River 25,415 8.5
Big Creek 6,415 2.2
Indian Creek 865 0.3
Bush River 20,470 6,9
b. Minor tributaries & immediate
drainage (non-point load) - 10,965 3.7
c. Known municipal STP's -
Batesburg 3,545 1.2
Clinton 8,960 3.0
Greenwood 36,690 12.3
Indirect input via
Lake Greenwood (13 plants) 78,285 26.3
Joanna Mills Village 2,075 0.7
Laurens 10,885 3.7
Leesville 905 0.3
Newberry
Ocona 8,635 2.9
Boundary St. 16,250 5.5
Gum Springs <5 <0.1
Pool #1 780 0.3
Ninety Six 2,720 0.9
Prosperity
#1 - S.W. 655 0.2
#2 - N.W. 1,450 0.5
Ridge Spring 565 0,2
Saluda 5,975 2.0
-------
17
kg P/ % of
Source ^r total
d. Septic tanks* - 1,425 0.5
e. Known industrial - ?
f. Direct precipitation** - 3,600 1.2
Total 297,105 100.0
2. Outputs -
Lake outlet - Saluda River 83,275
3. Net annual P accumulation - 213,830 kg.
* Estimate based on 5,000 lakeshore dwellings and three public access areas
with facilities (Campbell and Dean, 1976); see Working Paper No. 175.
** See Working Paper No. 175.
-------
18
C. Annual Total Nitrogen Loading - Average Year:
1. Inputs -
kg N/ % of
Source yr total
a. Tributaries (non-point load) -
Saluda River 889,000 32.1
Horse Creek 6,835 0.2
Hollow Creek 13,045 0.5
Clouds Creek 94,120 3.4
Richland Creek 21,325 0.8
Little Saluda River 184,570 6.7
Big Creek 67,360 2.4
Indian Creek 10,035 0.4
Bush River 140,365 5.0
b. Minor tributaries & immediate
drainage (non-point load) - 216,040 7.8
c. Known municipal STP's -
Batesburg 12,895 0.5
Clinton 26,870 1.0
Greenwood 119,035 4.3
Indirect input via Lake
Greenwood (13 plants) 577,830 20.8
Joanna Mills Village 6,225 0.2
Laurens 32,650 1.2
Leesville 2,720 0.1
Newberry
Ocona 9,350 0.3
Boundary St. 40,250 1.5
Gum Springs 15 <0.1
Pool #1 1,985 <0.1
Ninety Six 8,160 0.3
Prosperity
#1 - S.W. 1,445 <0.1
#2 - N.W. 1,535 <0.1
Ridge Spring 1,700 <0.1
Saluda 13,055 0.5
-------
19
% of
Source yr total
d. Septic tanks* - 53,360 1.9
e. Known industrial -
f. Direct precipitation** - 221.945 8.0
Total 2,773,720 100.0
2. Outputs -
Lake outlet - Saluda River 1,927,285
3. Net annual N accumulation - 846,435 kg.
D. Mean Annual Non-point Nutrient Export by Subdrainage Area:
Tributary kg P/km2/yr kg N/km2/yr
Saluda River 9 206
Horse Creek 17 335
Hollow Creek 29 291
Clouds Creek 35 394
Richland Creek 26 429
Little Saluda River 89 650
Big Creek 50 529
Indian Creek 36 418
Bush River 68 463
* Estimate based on 5,000 lakeshore dwellings and three public access areas
with facilities (Campbell and Dean, 1976); see Working Paper No. 175.
** See Working Paper No. 175.
-------
20
E. Yearly Loads:
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 1.45 1.04 13.5 4.1
Vollenweider phosphorus loadings
(9/m2/yr) based on mean depth and mean
hydraulic retention time of Lake Murray:
"Dangerous" (eutrophic loading) 0.70
"Permissible" (oligotrophic loading) 0.35
-------
21
V. LITERATURE REVIEWED
Anonymous, 1973. Survey questionnaires (Leesville, Newberry,
Prosperity, Batesburg waste treatment facilities). SC
Dept. of Health & Env. Contr., Columbia.
Atkinson, Reid, 1975. Personal communication (population served
and treatment type for City of Greenwood). SC Dept. of
Health & Env. Contr., Columbia.
Burn's, Bobby, 1973. Survey questionnaire (Belton waste treatment
facilities). Belton.
Campbell, William M., and John Mark Dean, 1976. Environmental
inventory of Lake Murray, South Carolina; volume one. Env.
Res. Ctr., Inc., Columbia.
Cox, Ray, 1973. Survey questionnaire (Honea Path waste treatment
facilities). Honea Path.
Crum, W. Bowman, 1973. Survey questionnaire (Greenville and
Williamston waste treatment facilities). SC Dept. of Health &
Env. Contr., Columbia.
Davis, W. A., 1973. Survey questionnaire (West Pelzer waste treatment
facilities). West Pelzer.
Foley, John R., 1976. Personal communication (permitted point sources
in Lake Murray drainage). SC Dept. of Health & Env. Contr.,
Columbia.
Martin, R. 0. R., and Ronald L. Hanson, 1966. Reservoirs in the United
States. Water Supply Paper No. 1838, U.S.G.S., Wash., DC.
Surber, Frank, 1973. Survey questionnaire (Ware Shoals waste treatment
facilities). Ware Shoals.
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.
Wright, Ann, 1974. Personal communication (loading rate of Little
Saluda River). SC Dept. of Health & Env. Contr., Columbia.
-------
VI. APPENDICES
APPENDIX A
LAKE RANKINGS
-------
LAKE DATA TO BE USED IN RANKINGS
LAKE
CODE LAKE NAME
4503 FISHING CREEK KESERVOI*
4504 LAKE GREENrfOOO
4505 LAKE HARTwELL
4506 LAKE MARION
4507 LAKE MURRAY
4508 LAKE ROBINSON
4510 LAKE WATEREE
4511 LAKE XYLIE
4512 LAKE MOULTRIE
4513 LAKE KEOWEE
4514 LAKE SECESSION
4515 SALUDA LAKE
4516 LAKE WILLIAM C. BOWEN
MEDIAN
TOTAL P
0.143
0.061
0.013
0.055
0.024
0.014
0.094
0.045
0.026
O.OOB
0.057
0.046
0.022
MEDIAN
INORG N
0.535
0.470
0.130
0.280
0.260
0.260
0.450
0.380
0.200
0.170
0.355
0.230
0.360
500-
MEAN SEC
483.000
H63.917
422.000
470.176
H24.905
458.778
475.667
462.222
455.36.
371.750
462.778
476.833
459.889
MEAN
CHLOHA
2.811
8.150
6.157
8.728
6.4':8
8.611
8.408
5.42?
6.800
2.d33
10.722
1.517
3.911
15-
MIN oc
10.20C
15.000
15.000
14.90C
15.000
14.000
14.100
14.800
11.200
15.000
15.000
10.800
15.000
MEDIAN
DI55 ORTnO P
0.051
0.011
0.004
0.010
0.007
0.005
0.034
0.013
O.OOb
0.003
0.006
0.006
0.007
-------
PERCENT OF LAKES WITH HIGHER VALUES (NUMBED OF LAKES WITH HIGHER VALUES)
LAKE
CODE LAKE NAME
4503 FISHING CHEEK RESERVOIR
4504 LAKE GREENWOOD
4505 LAKE. HARTWELL
4506 LAKE MARION
4507 LAKE MURRAY
4508 LAKE ROBINSON
4510 LAKE WATEHEE
4511 LAKE WYLIE
4512 LAKE MOULTRIE
4513 LAKE KEOWEE
4514 LAKE SECESSION
4515 SALUOA LAKE
4516 LAKE WILLIAM c. BOWEN
MEDIAN
TOTAL P
0 (
17 (
92 (
33 (
67 (
83 (
B <
50 (
58 (
100 (
?5 (
42 (
75 (
0)
2>
11)
4)
8)
10)
1)
6)
7)
12)
3)
5)
9)
MEDIAN
INORG N
0 (
P (
100 (
50 (
62 (
62 (
17 <
25 <
83 <
92 <
42 (
75 (
33 (
0)
1)
12)
6)
7)
7)
2)
3)
10)
11)
5)
9)
4)
500-
MEAN SEC
0 (
33 (
92 (
25 (
83 <
67 (
17 <
SO (
75 (
100 (
42 <
8 (
58 (
0)
4)
11)
3)
10)
8)
2)
6)
9)
12)
5)
1)
7)
MEAN
CHLORA
92 (
42 (
58 f
17 (
50 (
25 (
33 (
67 (
8 (
83 (
0 (
100 (
75 (
11)
5)
7)
2)
6)
3)
4)
S)
1)
10)
0)
12)
9)
15-
MIN DO
100 (
21 (
21 (
50 (
21 (
75 (
67 (
58 (
83 (
21 (
21 (
92 (
21 (
12)
0)
0)
6)
0)
9)
8)
7)
10)
0)
0)
11)
0)
MEDIAN
DISS OhlTHO P
0 (
25 (
92 (
33 (
46 (
83 (
8 (
17 (
71 (
100 (
58 (
71 (
46 (
0)
3)
11)
4)
5)
10)
1)
2)
6)
12)
7)
8)
5)
INDEX
NO
192
146
455
208
329
395
150
267
378
496
188
388
308
-------
LAKES RANKED BY INDEX NOS.
RANK LAKE CODE LAKE NAME INDEX NO
1 4513 LAKE KEOwEE 496
2 4505 LAKE HARTKELL 455
3 4508 LAKE ROBINSON 395
4 4515 SALUDA LAKE 388
5 4513 LAKE MOULTRIE 378
6 4507 LAKE MURRAY 329
7 4516 LAKE WILLIAM C. BOWEN 308
8 4511 LAKE WYLIE 267
9 4506 LAKE MARION 208
10 4503 FISHING CREEK RESERVOIR 192
11 4514 LAKE SECISS10N 188
12 4510 LAKE WATEREt 150
13 4504 LAKE GREENWOOD 146
-------
APPENDIX B
CONVERSION FACTORS
-------
CONVERSION FACTORS
Hectares x 2.471 = acres
Kilometers x 0.6214 = miles
Meters x 3.281 = feet
Cubic meters x 8.107 x 10"4 = acre/feet
Square kilometers x 0.3861 = square miles
Cubic meters/sec x 35.315 = cubic feet/sec
Centimeters x 0.3937 = inches
Kilograms x 2.205 = pounds
Kilograms/square kilometer x 5.711 = Ibs/square mile
-------
APPENDIX C
TRIBUTARY FLOW DATA
-------
TRIBUTARY FLOW INFORMATION FOR SOUTH CAROLINA
04/27/76
LAKE CODE 4507
LAKE MURRAY
TOTAL DRAINAGE AREA OF LAKE(SO "KM) 6?67.8
SUB-DRAINAGE
TRIBUTARY AREAISQ KM)
JAN
FEB
MAR
APR
MAY
NORMALIZED FLOwS(CMS)
JUN JUL AUG
SEP
OCT
NOV
OEC
SUMMARY
TOTAL ORAINAGK AREA OF LAKE
SUM OF SUB-DRAINAGE AREAS
MEAN MONTHLY FLOWS AND DAILY FLOWS(CMS)
6267.8
6063.5
TOTAL FLOW IN
TOTAL FLOW OUT
1044.11
1040.91
TRIBUTARY MONTH YEAR
4507A1
MEAN FLOW DAY
FLOW DAY
FLOW DAY
FLOW
4507A2
2
3
4
5
6
7
8
9
10
11
12
1
2
2
3
4
5
6
7
8
9
10
11
12
1
2
73
73
73
73
73
73
73
73
73
73
73
74
74
73
73
73
73
73
73
73
73
73
73
73
74
74
186.042
135.921
214.642
110.436
221.155
135.071
110.719
154.893
44.741
33.697
50.404
172.733
178.396
131.673
141.584
195.386
91.747
133.372
62.863
43.603
92.313
39.077
43.891
53.802
141.584
113.267
18
14
15
17
19
19
17
19
23
20
17
8
6
25
11
14
20
19
15
12
16
14
18
9
13
10
21.238
237.862
25.768
26.901
34.547
173.299
67.111
127.426
14.158
15.574
90.614
150.079
269.010
19.822
42.475
132.806
83.818
50.970
28.317
36.812
249.188
15.574
12.743
19.822
99.1C9
152.911
22
138.753
31
134.505
MEAN
4507A1
4S07A2
4507«1
4507C1
4507D1
450 7E1
4507F1
4507G1
4507H1
4507J1
45072Z
6267.8
4325.3
20.4
4^.8
238.8
49.7
284.1
127.4
24.0
303.0
644.9
94.25
75.04
0.453
0.99
5.30
1.10
6.31
2.83
0.538
6.71
14.67
98.95
91.75
0.651
1.44
7.76
1.61
9.23
4.13
0.765
9.80
21.44
106.14
111.85
0.765
1.67
8.98
1.87
10.70
4.79
0.906
11.36
24.81
101.99
90.61
0.461
1.08
5.72
1.19
6.80
3.06
0.566
7.22
15.80
62.47
59.75
0.198
0.42
2.29
0.48
2.72
1.22
0.227
2.89
6.31
82.37
48.70
0.113
0.25
1.39
0.28
1.64
0.74
0.142
1.76
3.82
86.79
46.72
0.142
0.31
1.59
0.34
1.90
0.85
0.170
2.01
4.39
92.87
43.61
0.113
0.25
1.30
0.28
1.56
0.71
0.142
1.64
3.60
79.88
38.79
0.085
0.17
0.93
0.20
1.10
0.51
0.085
1.19
2.61
79.05
41.34
0.113
0.23
1.19
0.25
1.42
0.62
0.113
1.50
3.28
75.73
41.91
0.142
0.31
1.59
0.34
1.90
0.85
0.170
2.01
4.39
80.43
53.80
0.255
0.54
2.89
0.59
3.45
1.56
0.283
3.68
8.01
86.66
61.82
0.291
0.63
3.39
0.71
4.03
1.81
0.340
4.28
9.36
-------
TRIBUTARY FLO* INFORMATION FOR SOUTH CAROLINA
04/27/76
LAKE CODE 4507
LAKE MURRAY
MEAN MONTHLY FLOKS AND DAILY FLOWS(CMS)
TRIBUTARY MONTH YEAR
MEAN FLOW DAY
FLOW DAY
FLOB DAY
FLOW
4507B1
4507C1
4507DI
4507E1
2
3
4
5
6
7
8
9
10
11
12
1
2
2
3
4
5
6
7
8
9
10
11
12
1
2
2
3
4
5
6
7
a
9
10
11
12
1
2
2
3
4
S
6
7
8
9
10
11
12
1
2
73
73
73
73
73
73
73
73
73
73
73
74
74
73
73
73
73
73
73
73
73
73
73
73
74
74
73
73
73
73
73
73
73
73
73
73
73
74
74
73
73
73
73
73
73
73
73
73
73
73
74
74
0.850
0.765
0.850
0.198
0.934
0.340
0.198
0.821
0.085
0.057
0.113
0.396
0.566
1.869
1.671
1.416
0.425
2.067
0.736
0.425
1.784
0.198
0.142
0.255
0.878
1.274
9.911
8.920
7.589
2.237
10.959
3.908
2.209
9.486
1.048
0.793
1.303
4.701
6.796
2.067
1.869
1.586
0.481
2.294
0.821
0.453
1.982
0.227
0.170
0.283
0.991
1.416
18
14
15
17
19
19
17
19
23
20
17
8
8
18
14
15
17
19
19
17
19
23
20
17
8
8
18
14
15
17
19
19
17
19
23
20
17
8
8
25
11
14
17
16
15
12
16
14
20
9
13
10
0.340
0.453
. 0.198
0.113
0.283
0.113
0.057
0.057
0.085
0.850
0.142
0.170
1.472
0.736
0.991
0.453
0.227
0.623
0.255
0.085
0.085
0.113
0.113
0.283
0.396
3.256
3.908
5.210
2.350
1.189
13.026
1.303
0.510
0.651
0.906
0.850
1.557
2.095
17.273
0.425
1.642
0.481
0.255
7.079
0.283
0.113
0.170
0.198
0.198
0.340
0.425
1.019
22
0.538
22
1.189
22
6.230
31
1.359
-------
TRIBUTARY FLOW INFORMATION FOR SOUTH CAROLINA
04/27/76
LAKE CODE 4507
LAKE MURRAY
MEAN MONTHLY FLOWS AND DAILY FLOWS(CMS)
TRIBUTARY MONTH YEAR
MEAN FLO1* DAY
FLO* DAY
FLOW DAY
FLOW
450 7F1
450701
4507H1
4507JI
2
3
4
5
6
7
8
9
10
11
12
1
2
2
3
4
5
6
7
8
9
10
11
12
1
2
2
3
4
5
6
7
8
9
10
11
1?
1
2
2
3
4
•5
f,
7
B
9
10
11
12
1
2
73
73
73
73
73
73
73
73
73
73
73
74
74
73
73
73
73
73
73
73
73
73
73
73
74
74
73
73
73
73
73
73
73
73
73
73
73
74
74
73
73
73
73
73
73
73
73
73
73
73
74
74
11.808
10.591
9.061
2.662
13.026
4.672
2.633
11.270
1.246
0.934
1.557
5.578
tt.070
5.295
4.757
4.049
1.189
5.862
2.095
1.189
5.069
0.566
0.425
0.708
2.52C
3.625
0.991
0.906
0.765
0.227
1.104
0.396
0.227
0.963
0.113
0.065
0.142
0.481
0.680
12.6C1
11.327
9.623
2.832
13.932
4.955
2.832
12.035
1.331
0.991
1.671
5.975
8.608
as
11
14
20
16
15
12
16
14
18
9
13
10
25
11
14
20
16
15
12
16
14
18
9
13
10
25
11
14
20
16
15
12
16
14
18
9
13
10
25
11
14
20
16
15
12
16
14
18
9
13
10
2.492
9.316
2.775
1.416
45.307
1.557
0.623
0.906
1.076
0.991
1.869
2.492
5.947
1.133
4.191
1.246
0.651
20.530
0.708
0.2S3
0.425
0.481
0.453
0.850
1.104
2.633
0.198
0.793
0.227
0.113
3.398
0.142
0.057
0.085
0.035
0.085
0.170
0.198
0.510
2.662
9.911
2.973
1.529
48.139
1.642
0.651
0.991
1.161
1.133
1.982
2.662
6.286
31
7.759
31
3.483
31
0.651
31
8.297
-------
TRIBUTARY FLO* INFORMATION FOR SOUTH CAROLINA
04/37/76
LAKE CODE 4507
LAKE MURRAY
MEAN MONTHLY FLOWS AND DAILY FLOWS(CMS)
TRIBUTARY
4507ZZ
MONTH YEAR
2
3
4
5
6
7
8
9
10
11
12
1
2
73
73
73
73
73
73
73
73
73
73
73
74
74
MEAN FLOW DAY
27.467
24.636
20.954
6.230
30.299
10.760
6.083
26.193
2.888
2.180
3.625
13.026
18.831
25
11
14
20
19
15
12
16
14
18
9
13
10
FLOW DAY
5.777
21.662
6.513
3.313
33.980
3.625
1.444
2.180
2.520
2.407
4.248
5.663 31
13.734
FLOW DAY
FLOW
18.123
-------
APPENDIX D
PHYSICAL and CHEMICAL DATA
-------
STORET RETRIEVAL DATE 76/04/27
DATE
FROM
TO
73/03/26
73/07/09
73/09/22
TIME
OF
DAY
11
11
11
11
11
11
11
11
11
11
11
11
10
10
10
10
10
10
10
10
10
10
10
10
10
10
10
10
00
00
00
00
00
00
00
00
00
00
00
00
50
50
50
50
50
50
50
50
50
30
30
30
30
30
30
30
DEPTH
FEET
0000
0006
0013
0020
0035
0050
0075
0100
0120
0140
0160
0179
0000
0006
0015
0030
0060
0090
0120
0150
0178
0000
0025
0040
0060
0110
0140
0175
00010
MATER
TEMP
CENT
13.3
13.3
12.3
12.1
12.0
11.3
10.6
10.1
9.9
9.9
9.6
9.3
30.2
30.1
29.8
24.2
19.3
15.9
15.2
14.8
14.4
27.0
26.8
26.1
22.5
19.5
18.6
17.6
450701
34 02 59.0 081 13 00.0 3
LAKE MURRAY
45063 SOUTH CAROLINA
030891
HEPALES 2111202
0183 FEET DEPTH CLASS 00
00300
00
M6/L
10.0
10.0
10.0
10.0
9.6
9.9
9.8
9.8
9.6
9.3
9.3
7.9
8.0
2.6
3.2
4.5
3.9
3.6
2.7
6.8
6.2
1.2
0.1
0.1
0.1
0.1
00077 00094
TRANSP CNDUCTVY
SECCHI FIELD
INCHES MICROMHO
72 70
65
65
65
70
70
70
70
65
65
65
65
108 63
60
60
63
63
63
63
68
102 57
55
51
56
57
72
102
00400
PH
SU
7.30
7.40
7.40
7.40
7.50
7.50
7.50
7.40
7.30
7.30
7.30
7.20
8.30
7.70
7.40
6.40
6.40
6.40
6.40
6.40
6.50
6.70
6.40
6.30
6.30
6.20
6.40
00410
T ALK
CAC03
MG/L
16
16
17
17
19
17
17
16
16
15
15
15
20
19
20
22
19
19
18
19
20
20
19
18
22
20
22
28
00610
NH3-N
TOTAL
MG/L
0.070
0.030
0.030
0.030
0.030
0.030
0.020
0.020
0.020
0.020
0.020
0.030
0.080
0.070
0.070
0.080
0.060
0.050
0.050
0.070
0.070
0.060
0.040
0.050
0.110
0.050
0.110
0.350
00625
TOT KJEL
N
MG/L
0.700
0.300
0.300
0.300
0.300
0.300
0.300
0.200
0.200
0.200
0.200
0.300
0.300
0.200
0.200K
0.200K
0.20 OK
0.200K
0.200K
0.200K
0.200K
1.000
0.400
0.400
0.400
0.300
0.400
0.700
00630
N02&N03
N-TOTAL
MG/L
0.210
0.180
0.190
0.190
0.190
0.220
0.240
0.250
0.260
0.260
0.270
0.270
0.060
0.050
0.060
0.130
0.280
0.360
0.390
0.420
0.430
0.030
0.020
0.030
0.030
0.190
0.080
0.020
00671
PHOS-DIS
ORTHO
MG/L P
0.007
0.005
0.004
0.004
0.004
0.004
0.004
0.005
0.006
0.006
, 0.007
0.011
0.003
0.004
0.004
0.003
0.005
0.005
0.005
0.007
0.006
0.013
0.009
0.010
0.010
0.008
O.OOB
0.026
K 1/AL'JE KNOWN TO BE
LESS THAN INDICATED
-------
STORE! RETRIEVAL DATE 76/04/27
DATE
FROM
TO
73/03/26
73/07/09
73/09/22
TIME DEPTH
00665
PHOS-TOT
OF
DAY
11
11
11
11
11
11
11
11
11
11
11
11
10
10
10
10
10
10
10
10
10
10
10
10
10
10
10
10
FEET
00 0000
00 0006
00 0013
00 0020
00 0035
00 0050
00 0075
00 0100
00 0120
00 0140
00 0160
00 0179
50 0000
50 0006
50 0015
50 0030
50 0060
50 0090
50 0120
50 0150
50 0178
30 0000
30 0025
30 0040
30 0060
30 0110
30 0140
30 0175
MG/L P
0.027
0.023
0.021
0.018
0.019
0.018
0.024
0.025
0.025
0.026
0.026
0.032
0.012
0.014
0.012
0.011
0.012
0.012
0.012
0.019
0.031
0.019
0.015
0.019
0.020
0.011
0.017
0.044
32217
CHLRPHYL
A
UG/L
4.8
6.0
5.0
450701
34 02 59.0 081 13 00.0 3
LAKE MURRAY
45063 SOUTH CAROLINA
030891
11EPALES 2111202
0183 FEET DEPTH CLASS 00
-------
STORET RETRIEVAL DATE 76/04/27
DATE
FROM
TO
73/03/26
73/07/09
73/09/22
TIME DEPTH
OF
DAY FEET
12 10 0000
12 10 0006
12 10 0013
12 10 0020
12 10 0035
12 10 0050
12 10 0070
12 10 0090
12 10 0110
12 10 0128
10 00 0000
10 00 0006
10 00 0015
10 00 0030
10 00 0055
10 00 0080
10 00 0100
10 00 0120
10 00 0136
11 25 0000
11 25 0025
11 25 0040
11 25 0055
11 25 0090
11 25 0132
00010
WATER
TEMP
CENT
13.0
12.6
12.6
12.6
12.1
11.0
10.6
10.1
9.8
9.6
29.7
29.7
29.0
23.8
19.4
16.6
15.5
15.0
14.9
27.0
26.7
26.6
23.9
20.2
18.5
450702
34 04 00.0 081 16 40.0 3
LAKE MURRAY .
45063 SOUTH CAROLINA
030891
11EPALES 2111202
0142 FEET DEPTH CLASS 00
00300
DO
MG/L
10.0
10.0
10.0
9.8
9.6
9.8
9.6
9.6
9.2
7.9
7.1
1.1
2.6
3.6
3.5
3.1
3.4
7.6
6.6
5.8
0.0
0.1
0.2
00077 00094
TRANSP CNDUCTVY
SECCHI FIELD
INCHES MICROMHO
72 68
68
72
68
68
68
65
65
65
68
108 63
60
60
62
65
65
65
65
68
102 55
55
55
61
56
62
00400
PH
SU
7.20
7.40
7.40
7.50
7.50
7.50
7.50
7.50
7.30
7.30
8.00
7.60
7.00
6.30
6.40
6.40
6.40
6.40
6.40
6.50
6.70
6.30
6.50
6.30
6.30
00410
T ALK
CAC03
MG/L
16
16
17
17
17
16
16
15
14
14
17
15
15
17
22
20
19
18
21
22
21
18
24
23
23
00610
Nrt3-N
TOTAL
MG/L
0.040
0.030
0.030
0.030
0.030
0.020
0.030
0.010
0.020
0.030
0.080
0.080
0.110
0.070
0.060
0.060
0.060
0.060
0.090
0.050
0.040
0.060
0.130
0.130
0.280
00625
TOT KJEL
N
MG/L
0.500
0.400
0.300
0.300
0.300
0.300
0.300
0.300
0.400
0.300
0.400
0.300
0.200
0.200K
0.200K
0.200K
0.200K
0.200K
0.200
0.800
0.400
0.400
0.400
0.500
0.700
00630
N02&N03
N-TOTAL
MG/L
0.190
0.190
0.190
0.190
0.200
0.230
0.250
0.260
0.280
0.290
0.060
0.060
0.120
0.190
0.350
0.360
0.400
0.410
0.430
0.030
0.020
0.030
0.020
0.020
0.020
00671
PHOS-DIS
ORTHO
MG/L P
0.005
0.007
0.004
0.004
0.003
0.004
0.004
0.005
0.006
0.006
0.004
0.004
0.005
0.010
0.004
0.004
0.005
0.006
0.005
0.006
0.004
0.010
0.007
0.010
0.031
K VALUE KNOWN ro at
LESS THAN INDICATED
-------
STORE! RETRIEVAL DATE 76/04/27
DATE
FROM
TO
73/03/26
73/07/09
73/09/22
00665 32217
TIME DEPTH PHOS-TOT CHLRPHYL
OF A
DAY FEET
12
12
12
12
12
12
12
12
12
12
10
10
10
10
10
10
10
10
10
11
11
11
11
11
11
10
10
10
10
10
10
10
10
10
10
00
00
00
00
00
00
00
00
00
25
25
25
25
?5
25
0000
0006
0013
0020
0035
0050
0070
0090
0110
0128
0000
0006
0015
0030
0055
0080
0100
0120
0136
0000
0025
0040
0055
0090
0132
MG/L P
0.021
0.025
0.018
0.023
0.019
0.021
0.024
0.025
0.029
0.033
0.013
0.015
0.015
0.013
0.012
0.012
0.015
0.014
0.023
0.010
0.011
0.011
0.013
0.018
0.037
UG/L
4.9
607
4.8
450702
34 04 00.0 081 16 40.0 3
LAKE MURRAY
45063 SOUTH CAROLINA
030891
11EPALES
0142 FEET
2111202
DEPTH CLASS 00
-------
STORET RETRIEVAL DATE 76/04/27
DATE
FROM
TO
73/03/28
73/07/09
73/09/22
00010
TIME DEPTH WATER
OF TEMP
DAY FEET
08
08
08
08
08
08
12
12
12
12
12
12
12
12
13
13
13
13
13
13
13
20
20
20
20
?0
20
SO
50
50
50
50
50
50
50
30
30
30
30
30
30
30
0000
0004
0015
0050
0075
0114
0000
0006
0015
0030
0055
0075
0095
0116
0000
0025
0040
0050
0075
0100
0130
CENT
13
13
13
11
11
10
31
30
29
23
19
16
15
14
27
26
26
24
21
19
18
.0
.1
.0
.8
.0
.5
.0
.0
.4
.7
.7
.8
.5
.8
.0
.7
.5
.9
.3
.6
.4
450703
34 03 05.0 081 18 45.0 3
LAKE MURRAY
45063 SOUTH CAROLINA
030891
11EPALES
2111202
0118 FEET DEPTH CLASS
00300
00
MG/L
10.4
9.8
9.0
9.0
8.8
7.9
6.4
0.8
2.8
3.7
2.7
1.7
7.1
6.2
5.6
0.1
0.0
0.0
0.0
00077 00094
TRANSP CNOUCTVY
SECCHI FIELD
INCHES MICROMriO
54 65
65
65
65
65
65
96 69
60
60
63
64
65
63
69
102 54
53
56
63
60
58
70
00400
PH
SU
7.70
7.70
7.60
7.60
7.60
7.50
7.80
7.70
7.20
6.30
6.40
6.40
6.30
6.30
6.60
6.59
6.60
6.40
6.40
6.40
6.50
00410
T ALK
CAC03
MG/L
17
16
16
16
17
16
19
15
17
17
18
19
18
22
19
22
22
24
23
23
26
00610
NH3-N
TOTAL
MG/L
0.070
0.040
0.030
0.030
0.030
0.030
0.080
0.050
0.100
0.070
0.060
0.060
0.060
0.080
0.080
0.030
0.040
0.140
0.190
0.220
0.490
00
00625
TOT KJEL
N
MG/L
0.300
0.200K
0.200K
0.200K
0.200K
0.300
0.400
0.400
0.400
0.200
0.300
0.200K
0.200
Oo200K
0.800
0.300
0.300
0.500
0.500
0.500
0.900
00630
N02&N03
N-TOTAL
MG/L
0.230
0.220
0.230
0.270
0.280
0.280
0.060
0.040
0.130
0.250
0.280
Oo340
Oo390
0.440
0.030
Oo020
0.020
0.020
0.020
0.040
0.020
00671
PHOS-DIS
ORTHO
MG/L P
0.009
0.007
0.007
0.007
0.006
0.006
0.009
Oo004
0.006
0.004
0.004
0.005
0.006
0.008
0.007
0.006
0.005
0.008
0.014
0.026
0.050
K VALUE KNOWN TO BE
LESS THAN INDICATED
-------
STORET RETRIEVAL DATE 76/04/27
00665 32317
DATE TIME DEPTH PHOS-TOT CHLRPHYL
FROM OF A
TO DAY FEET MG/L P UG/L
73/03/28 OB 20 0000 0.028 5.9
08 20 0004 0.031
08 20 0015 0.031
08 20 0050 0.028
08 20 0075 0.028
08 20 0114 0.051
73/07/09 12 50 0000 0.015 7.4
12 50 0006 0.014
12 50 0015 0.007
12 50 0030 0.016
12 50 0055 OoOll
12 50 0075 0.014
12 50 0095 OoOlS
12 50 0116 0«024
73/09/22 13 30 0000 0.012 5.4
13 30 0025 Oo012
13 30 0040 0»013
13 30 0050 0«027
13 30 0075 0.022
13 30 0100 0.029
13 30 0130 0.053
450703
34 03 05.0 081 18 45.0 3
LAKE MURRAY
45063 SOUTH CAROLINA
030891
11EPALES
0118 FEET
DEPTH
2111202
CLASS 00
-------
STORE! RETRIEVAL DATE 76/04/27
DATE
FROM
TO
73/03/28
73/07/09
73/09/22
TIME
OF
DAY
09
09
09
09
09
09
14
14
14
14
14
14
14
14
14
14
14
14
14
10
10
10
10
10
10
15
15
15
15
15
15
15
20
20
20
20
20
20
DEPTH
FEET
0000
0004
0015
0040
0075
0102
0000
0006
0015
0030
0055
0080
0106
0000
0020
0035
0055
0070
0087
00010
WATER
TEMP
CENT
13.6
13.7
13.7
13.2
11.4
11.3
30.9
29.7
27.6
23.4
19.5
16.1
15.0
27.4
27.0
26.5
25.0
21.8
20.2
450704
34 04 00.0 081 22 35.0 3
LAKE MURRAY
45063 SOUTH CAROLINA
030891
11EPALES 2111202
0106 FEET DEPTH CLASS 00
00300
00
MG/L
8.8
8.8
9.0
8.8
8.8
8.2
4.5
0.4
1.6
0.7
0.6
7.6
5.4
2.2
0.1
0.0
0.0
00077
TRANSP
SECCHI
INCHES
30
84
90
00094
CNDUCTVY
FIELD
MICROMHO
65
60
70
60
63
65
63
60
60
60
69
71
71
49
48
51
56
67
69
00400
PH
SU
7.70
7.50
7.70
7.70
7.50
7.60
8.20
7.30
6.40
6.20
6.30
6.40
6.40
6.60
6.60
6.40
6.30
6.50
6.50
00410
T ALK
CAC03
MG/L
13
12
10K
10K
12
14
20
19
19
18
19
23
22
20
21
22
24
25
30
00610
NH3-N
TOTAL
MG/L
0.070
0.050
0.050
0.050
0.030
0.040
0.070
0.050
0.170
0.150
0.060
0.130
0.120
0.050
0.040
0.110
0.230
0.550
0.660
00625
TOT KJEL
N
MG/L
0.700
0.300
0.300
0.200
0.200
0.200
0.400
0.300
0.400
0.400
0.800
0.800
0.900
0.700
0.300
0.400
0.600
1.000
1.200
00630
N02&N03
N-TOTAL
MG/L
0.320
0.320
0.190
0.190
0.300
0.310
0.050
0.040
0.190
0.230
0.410
0.380
0.370
0.030
0.030
0.040
0.060
0.030
0.030
00671
PHOS-OIS
ORTHO
MG/L P
0.017
0.014
0.015
0.014
0.010
0.012
0.003
0.004
0.010
0.008
0.006
0.008
0.007
0.010
0.011
0.008
0.009
0.035
0.050
K VALUE KNOWN TO BE
LESS THAN INDICATED
-------
STORE! RETRIEVAL DATE 76/64/27
00665
DATE TIME DEPTH PHOS-TOT
FROM OF
TO DAY FEET MG/L P
73/03/28 09
09
09
09
09
09
73/07/09 14
14
14
14
14
14
14
73/09/22 14
14
14
14
14
14
10 0000
10 0004
10 0015
10 0040
10 0075
10 0102
15 0000
15 0006
15 S015
15 0030
15 0055
15 0080
15 0106
20 0000
20 0020
20 0035
20 0055
20 0070
20 0087
0.059
0.052
0.056
0.052
0.031
0.049
0.015
0.016
0.040
0.039
0.049
Oo923
32217
CHLRPHYL
A
UG/L
4.9
@o@20
00025
00027
Oo052
0.048
0»073
9o7
509
450704
34 04 OOoO 081 22 35.0 3
LAKE MURRAY
45063 SOUTH CAROLINA
030891
HEPALES 2111202
0106 FEET DEPTH CLASS 00
-------
STOHET RETRIEVAL DATE 76/04/27
450705
34 05 40.0 081 27 40.0 3
LAKE MURRAY
45071 SOUTH CAROLINA
030891
DATE
FROM
TO
73/03/28
73/07/09
73/09/22
TIME
OF
DAY
10
10
10
10
10
14
14
14
14
14
14
15
15
15
15
15
00
00
00
00
00
45
45
45
45
45
45
00
00
00
00
00
DEPTH
FEET
0000
0004
0015
0035
0050
0000
0006
0015
0028
0040
0056
0000
0015
0025
0040
0056
00010
WATER
TEMP
CENT
14.6
14.6
14.6
13.9
12.5
31.1
30.3
27.1
24.4
22.5
18.2
27.8
27.1
26.4
25.7
25.0
00300
DO
MG/L
8.8
8.8
8.2
7.6
8.6
2.1
0.3
0.5
1.1
6.4
6.8
1.6
1.5
00077 00094
TRANSP CNDUCTVY
SECCHI FIELD
INCHES MICROMMO
29 60
58
60
61
60
60 62
55
60
65
70
75
72 49
53
56
57
72
11EPALES 2111202
0055 FEET DEPTH CLASS 00
00400 00410 00610 00625
PH T ALK NH3-N TOT KJEL
SU
7.80
7.60
7.60
7.60
7.60
8.30
7.40
6.40
6.30
6.40
6.60
6.70
6.80
6.40
6.60
6.40
CAC03
MG/L
10K
11
12
13
13
17
14
18
19
20
24
23
22
23
22
30
TOTAL
M6/L
0.070
0.060
0.050
0.060
0.060
0.090
0.070
0.100
0.400
0.380
0.280
0.050
0.040
0.130
0.160
0.540
N
MG/L
0.500
0.300
0.200
0.300
0.300
0.500
0.600
0.600
1.000
0.700
0.500
0.500
0.400
0.400
0.200
0.900
00630
N02&N03
N-TOTAL
MG/L
0.350
0.360
0.350
0.340
0.340
0.060
0.060
0.080
0.110
0.110
0.140
0.030
0.030
0.060
0.100
0.040
00671
PHOS-OIS
ORTHO
MG/L P
0.020
0.019
0.019
0.017
0.017
0.011
0.008
0.009
0.026
0.020
0.009
0.010
0.013
0.013
0.012
0.013
00665 32217
DATE TIME DEPTH PHOS-TOT CHLRPHYL
FROM OF A
TO DAY FEET MG/L P UG/L
73/03/26
73/07/09
73/09/22
10 00
10 00
10 00
10 00
10 00
14 45
14 45
14 45
14 2.5
14 45
14 45
15 00
15 00
15 00
15 00
15 00
0000
0004
0015
0035
0050
0000
0006
0015
0028
0040
0056
0000
0015
0025
0040
0056
0.067
0.065
0.061
0.064
0.061
0.028
0.030
0.029
0.092
0.064
0.036
0.027
0.023
0.028
0.039
0.060
6.2
7.5
10.1
K, \MLUE MMOWN TO BE
LtSS THAN INDICATED
-------
STORE! RETRIEVAL DATE 76/04/27
450706
34 05 OOoO 081 32 15,0 3
LAKE MURRAY
45081 SOUTH CAROLINA
030891
DATE
FROM
TO
73/03/26
73/07/09
73/09/22
DATE
FROM
TO
73/03/26
73/07/09
73/09/22
TIME DEPTH
OF
OAV FEET
is 45 eeoe
15 45 Oi906
15 45 0015
15 45 0023
15 10 0000
IS 10 0006
15 10 0015
15 10 0030
15 35 6900
15 35 0010
15 35 0020
15 35 0030
TIME DEPTH
OF
DAY FEET
15 45 0000
15 45 0006
15 45 0015
15 45 0023
15 10 0000
15 10 0006
15 10 0015
15 10 0030
15 35 0000
15 35 0010
15 35 0020
15 35 0030
00010
bATER
TEMP
CENT
14,7
14o4
I4o3
14,2
30o6
29,4
27»1
24,0
28,0
25,9
25,3
25,7
00665
PHOS-TOT
MG/L P
0,093
0,080
0,069
0,057
0,035
0,042
0,041
0,084
0,049
0,044
0,044
0,050
0630®
DO
MG/L
9,0
9,0
8,8
7,7
3,5
0,6
9,0
5,2
2,0
2,0
32217
CHLRPHYL
A
UG/L
8,4
404
9,3
00077 00094
TRANSP CNDUCTVY
SECCHI FIELD
INCHES MICROMHO
20 60
60
60
60
48 60
60
62
75
40 57
57
60
62
11EPALES 2111202
0027 FEET DEPTH CLASS 00
00400 00410 00610 00625
PH
SU
7,20
7,20
7,20
7,20
8,40
7,10
6,50
6,40
8,30
7,00
6,50
6o40
T ALK
CAC03
MG/L
12
13
14
13
21
21
22
22
21
23
24
22
NH3=N
TOTAL
MG/L
0,080
OoOSO
0,040
0,040
0,090
0,070
0,120
0,340
0,040
0,070
0,180
Oo200
TOT
N
KJEL
MG/L
0
0
0
0
0
0
0
0
0
0
0
0
,300
°400
0400
,400
,700
,600
,400
,800
,700
,200
o300
o300
00630
N02&N03
N-TOTAL
MG/L
0,340
0,370
0,390
Oo380
0,070
0,060
0,180
0,100
0,030
0,120
0,130
0,130
00671
PHOS-DIS
ORTHO
MO/L P
0,023
Oo019
0,019
0,019
0,005
0,009
0,011
0,019
0,010
0,009
0,012
0,012
-------
STORET RETRIEVAL DATE 76/04/27
450707
34 06 00.0 081 15 25.0 3
LAKE MURRAY
4506J SOUTH CAROLINA
030891
11EPALES 2111202
0068 FEET DEPTH CLASS 00
DATE
FROM
TO
73/03/27
73/07/09
73/09/22
DATE
FROM
TO
73/03/27
73/07/09
73/09/22
TIME DEPTH
OF
UAY FEET
15 15 0000
15 15 0004
15 15 0015
15 15 0040
15 15 0064
13 35 0000
13 35 0006
13 35 0015
13 35 0030
13 35 0048
13 35 0064
16 10 0000
16 10 0025
16 10 0040
16 10 0050
16 10 0060
16 10 0086
TIME DEPTH
OF
DAY FEET
15 15 0000
15 15 0004
15 15 0015
15 15 0040
15 15 0064
13 35 0000
13 35 0006
13 35 0015
13 35 0030
13 35 0048
13 35 0064
16 10 0000
16 10 0025
16 10 0040
16 10 0050
16 10 0060
16 10 0086
00010
WATER
TEMP
CENT
15.3
14.6
13.5
13.1
11.7
30.2
29.8
26.4
24.1
21.2
18.3
27.8
26.7
26.4
25.4
22.4
20.3
00665
PHOS-TOT
MG/L P
0.028
0.030
0.024
0.023
0.026
0.012
0.013
0.013
0.012
0.011
0.012
0.012
0.012
0.017
o.oia
0.016
0.015
00300
DO
MG/L
10.1
9.8
9.8
9.3
8.2
6.5
1.7
1.5
2.9
8.6
4.6
0.4
0.4
0.0
0.1
32217
CHLRPHYL
A
UG/L
5.0
8.1
5.0
00077 00094
TRANSP CNDUCTVY
SECCHI FIELD
INCHES MICSOMHO
72 78
70
70
70
72
96 63
60
60
63
65
69
120 51
52
52
51
56
62
00400
PH
SU
7
7
7
7
7
8
7
7
6
6
6
6
6
6
6
6
6
.80
.90
.90
.90
.90
.30
.60
.20
.40
.30
.40
.80
.40
.40
.50
.60
.60
00410
T ALK
CAC03
MG/L
10K
10K
10K
10K
10K
17
16
16
16
25
25
18
20
17
26
30
30
00610
NH3-N
TOTAL
MG/L
0.040
0.040
0.030
0.040
0.030
0.070
0.080
0.080
0.070
0.060
0.090
0.050
0.060
0.110
0.420
0.410
0.350
00625
TOT KJEL
N
MG/L
0.400
0.200
0.200
0.200K
0.200K
0.800
0.800
0.800
0.600
0.600
0.600
0.400
0.200K
0.300
0.500
0.600
0.500
00630
N02&N03
N-TOTAL
MG/L
0.190
0.180
0.180
0.190
0.220
0.040
0.070
0.060
0.190
0.310
0.330
0.030
0.030
0.030
0.020
0.020
0.020
00671
PHOS-DIS
ORTHO
MG/L P
0.008
0.007
0.005
0.006
0.006
0.003
0.004
0.004
0.004
0.007
0.006
0.006
0.008
0.009
0.013
0.011
0.011
K. Vf'LUE. KNOWN TO dt
LtiS FHAN INDICATED
-------
APPENDIX E
TRIBUTARY and WASTEWATER
TREATMENT PLANT DATA
-------
STORE! RETRIEVAL DATE 76/04/27
4507A1
34 02 30.0 081 11 30.0 4
SALUDA RIVER
45 LEXINGTON CO HWY
0/LAKE MURRAY 030891
BANK AT END OF RO 1.5 MI 8ELO DAM
HEPALES 2111204
0000 FEET DEPTH CLASS 00
DATE
FROM
TO
73/02/18
73/03/14
73/04/15
73/05/17
73/06/19
73/07/19
73/08/17
73/09/19
73/10/23
73/11/20
73/12/17
74/01/08
74/01/22
74/02/08
00630 00625
TIME DEPTH N02&.N03 TOT KJEL
OF N-TOTAL N
DAY FEET
09
13
10
10
09
12
09
13
10
12
08
13
09
09
45
45
45
30
15
50
00
15
00
45
30
45
00
30
MG/L
0
0
0
0
0
0
0
0
0
0
0
0
0
0
.170
.230
.280
.280
.380
.350
.210
.048
.029
.100
.160
.192
.260
.216
MG/L
0.
0.
1.
0.
0.
0.
0.
0.
1.
0.
0.
0.
0.
270
500
100
985
810
210
280
880
050
250
300
200
100K
0.200
00610 00671 00665
NH3-N PHOS-DIS PHOS-TOT
TOTAL ORTHO
MG/L
0
0
0
0
0
0
0
0
0
0
0
0
0
0
.019
.017
.047
.030
.038
.012
.088
.210
.490
.056
.016
.016
.012
.012
MG/L
0.
0.
0.
0.
0.
0.
0.
p
006
012
010
020
014
021
006
0.017
0.
0.
0.
0.
0.
0.
046
005K
008
012
012
005
MG/L P
0.025
0.025
0.035
0.050
0.025
0.021
0.015
0.040
0.060
0.020
0.045
0.030
0.040
0.005
K VALUE KNOWN fO BE
LESS THAN INDICATED
-------
STORET RETRIEVAL DATE 76/04/27
4507A2
34 08 30.0 081 37 30.0 4
SALUOA RIVER
45 SALUDA CO HWY MA
I/LAKE MURRAY 030891
ST hNY 395 BRDG 3 MI NE OF PERRY5 XROADS
11EPALES 2111204
0000 FEET DEPTH CLASS 00
DATE
FROM
TO
73/02/25
73/03/11
73/04/14
73/05/20
73/06/16
73/07/15
73/08/12
73/09/16
73/10/14
73/11/18
73/12/09
74/01/13
74/01/31
74/02/10
00630 00625
TIME DEPTH N02&N03 TOT KJEL
OF N-TOTAL N
DAY FEET
14
14
09
14
14
14
09
13
14
11
14
13
11
14
30
15
30
00
38
00
45
55
25
05
35
25
20
10
MG/L
0
0
0
0
0
0
0
0
0
0
0
0
0
0
.400
.399
.350
.280
.198
• 010K
.088
.081
.154
.280
.312
.470
.380
.480
MG/L
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
1.
0.
380
660
330
360
790
510
370
720
850
500
600
300
000
600
00610 00671 00665
NH3-N PHOS-DIS PHOS-TOT
TOTAL ORTHO
MG/L
0.098
0.075
0.060
0.048
0.063
0.014
0.048
0.072
0.120
0.080
0.084
C.060
0.060
0.110
MG/L
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
p
037
040
041
028
060
014
010
025
015
052
016
052
040
0.040
MG/L P
0
0
0
0
0
.085
.085
.085
.055
.135
0.075
0
0
0
0
0
0
0
0
.055
.180
.075
.052
.035
.100
.110
.095
K VALUE KNOWN 10 at
LESS THAN INDICATED
-------
STORE! RETRIEVAL DATE 76/04/27
4507B1
33 59 30.0 081 26 30.0 4
HORSE CREEK
45 LEXINGTON CO HWY
T/LAKE MURRAY 030991
ST HWY 158 8ROG <».5 MI NNW OF GILBERT
11EPALES 2111204
0000 FEET DEPTH CLASS 00
DATE
FROM
TO
73/02/18
73/03/14
73/04/15
73/05/17
73/06/19
73/07/19
73/08/17
73/09/19
73/10/23
73/11/20
73/12/17
74/01/08
74/01/22
74/02/08
00630 00625
TIME DEPTH N02&N03 TOT KJEL
OF N-TOTAL N
DAY FEET
10
14
12
11
09
13
09
13
10
13
09
14
09
10
45
40
00
00
45
25
30
50
30
30
00
15
40
00
MG/L
0
0
0
0
0
0
0
0
0
.660
.390
.430
.336
.450
.290
.240
.150
.176
0.084
0
0
0
0
.390
.560
.470
.470
MG/L
0.
0.
0.
1.
0.
0.
0.
280
480
250
200
460
240
220
0.330
0.
0.
0.
0.
0.
0.
300
200
300
400
100
400
00610 00671 00665
NH3-N PHOS-DIS PHOS-TOT
TOTAL ORTHO
MG/L
0
0
0
0
0
0
0
0
0
0
0
0
0
0
.024
.019
.009
.028
.028
.024
.019
.026
.037
.018
.020
.032
.024
.030
MG/L
0.
0.
0.
0*
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
p
009
015
Oil
018
026
032
018
020
015
012
016
016
020
025
MG/L P
0.025
0.045
0.030
0.030
0.050
0.040
0.035
0.040
0.020
0.025
0.030
0.040
0.055
0.060
-------
STORET RETRIEVAL DATE 76/04/27
4507C1
33 59 30.0 081 26 00.0 4
HOLLOW CREEK
45 LEXINGTON CO HWY
T/LAKE MURRAY 030991
ST HWY 54 8RDG 1 MI FROM MOUTH OF CREEK
11EPALES 2111204
0000 FEET DEPTH CLASS 00
DATE
FROM
TO
73/02/18
73/03/14
73/04/15
73/05/17
73/06/19
73/07/19
73/08/17
73/09/19
73/10/23
73/11/20
73/12/17
74/01/08
74/01/22
7^/02/08
00630 00625
TIME DEPTH N02&N03 TOT KJEL
OF N-TOTAL N
DAY FEET
11
14
11
11
09
13
09
14
13
09
14
10
10
00
25
50
10
55
35
40
00
40
15
25
00
10
MG/L
0
0
0
0
0
0
0
.250
.160
.126
.220
.180
.230
.220
0.098
0
0
0
0
0
0
.056
.012
.240
.156
.152
.152
MG/L
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
460
580
330
540
280
440
420
800
350
800
400
400
500
00610 00671 00665
NH3-N PHOS-DIS PHOS-TOT
TOTAL ORTHO
MG/L
0
0
0
0
•
•
•
•
036
024
019
046
0.058
0
0
0
0
0
0
0
c
0
•
•
•
•
•
•
•
•
•
032
034
021
036
028
112
032
028
045
MG/L P
0.012
0.029
0.014
0.015
0.024
0.025
0.021
0.019
0.025
0.016
0.048
0.024
0.020
0.045
MG/L P
0.03b
0.065
0.040
0.055
0.045
0.065
0.050
0.105
0.035
0.080
0.065
0.085
0.100
-------
STORE! RETRIEVAL DATE 76/04/27
4507D1
34 02 30.0 081 34 00.0 4
CLOUDS CREEK
45 SALUDA CO HWY MA
T/LAKE MURRAY 030891
ST HWY 25 BRDG 7.5 Ml N OF BATESBURG
11EPALES 2111204
0000 FEET DEPTH CLASS 00
DATE
FROM
TO
73/02/18
73/03/14
73/04/15
73/05/17
73/06/19
73/07/19
73/08/17
73/09/19
73/10/23
73/11/20
73/12/17
74/01/08
74/01/22
74/02/08
00630 00625
TIME DEPTH N02&N03 TOT KJEL
OF N-TOTAL N
DAY FEET
11
14
11
11
10
13
i©
14
11
14
09
14
10
10
15
55
30
30
10
50
05
15
20
00
30
40
10
30
MG/L
0
0
0
0
9
0
0
0
0
0
0
0
0
0
.530
.330
.410
«010K
.084
.©10K
.210
• Oil
<»336
.430
e590
.540
.390
.280
MG/L
0.520
@»93©
1.200
©.70®
0.696
0.7S0
Q0720
0.750
0.600
0.700
0.600
0.650
0.700
00610 00671 00665
NH3-N PHOS-D1S PHOS-TOT
TOTAL ORTHO
MG/L
0.069
0.
0.
0.
0.
©0
9o
60
00
0.
0.
0.
0.
0.
066
132
014
15®
016
@40
008
030
032
200
084
076
045
MG/L P
0
0
0
0
©
.034
.048
*040
oOlO
o§34
0.012
0
0
0
0
0
0
0
0
.036
.012
.074
.092
.184
.072
.068
.060
MG/L P
0
0
0
0
©
0
0
0
0
0
0
0
0
0
e080
olOS
0085
0075
oIlO
0070
0135
o085
.145
.175
.220
.140
.168
.115
K VALUE KNOWN TO BE
LESS THAN INDICATED
-------
STORE! RETRIEVAL DATE 76/04/37
4507E1
34 02 30.0 081 41 30.0 4
RICHLAND CREEK
45 SALUDA CO HWY MA
T/LAKE MURRAY 030891
ST HWY 39 8RDG 4 MI NE OF SALUDA
11EPALES 2111204
0000 FEET DEPTH CLASS 00
DATE
FROM
TO
73/02/25
73/03/11
73/04/14
73/05/17
73/06/16
73/07/15
73/08/12
73/09/16
73/10/14
73/11/20
73/12/09
7<»/01/13
74/01/31
74/02/10
TIME DEPTH
OF
DAY FEET
13 25
13 20
08 45
13 00
14 00
13 10
09 00
13 00
13 45
10 3®
13 40
12 45
10 20
13 30
00630
N02&N03
N-TOTAL
MG/L
0.120
0.110
0.078
0.273
0.147
0.240
0.290
0.028
OoOiOK
00@12
0.024
Oo@68
00224
00208
00625
TOT KJEL
N
MG/L
0.190
0.540
0.180
1.000
1.050
0.270
2.200
0.520
60 650
©o600
1.900
0.400
0,700
1.100
00610
NH3-N
TOTAL
MG/L
0.036
0.013
0.010
0.012
0.036
0.015
0.069
Oo014
©.056
Oo024
0.252
0.016
0.052
0.040
00671
PHOS-DIS
ORTHO
MG/L P
0.011
0.028
0.018
0.015
0.079
0.012
0.029
0.016
0.008
0.020
0.012
Oo032
0.060
0.040
00665
PHOS-TOT
MG/L P
0.020
0.055
0.030
0.035
0,160
0,040
Oo065
Oo045
00035
Oo070
Oo020
OoQ55
0.095
0.070
K VALUE KNOWN TO BE
LESS THAN INDICATED
-------
STORET RETRIEVAL DATE 76/04/27
4507F1
34 02 30.0 081 42 00.0 4
LITTLE SALUOA RIVER
45 SALUOA CO H«Y MA
T/LAKE MURRAY 030891
ST HWY 39 BRDG 4 MI NE OF SALUOA
11EPALES 2111204
0000 FEET DEPTH CLASS 00
DATE
FROM
TO
73/02/25
73/03/11
73/04/14
73/05/20
73/06/16
73/07/15
73/08/12
73/09/16
73/10/14
73/11/18
73/12/09
74/01/13
74/01/31
74/02/10
00630 00625
TIME DEPTH N02&N03 TOT KJEL
OF N-TOTAL N
DAY FEET
13
13
08
13
14
13
09
13
13
10
13
12
10
13
40
30
55
10
05
15
10
15
55
35
45
55
30
35
MG/L
0
0
0
0
0
0
0
0
0
0
0
0
0
0
.240
.240
.198
.740
.147
.640
.480
.378
.294
.360
.264
.384
.192
.208
MG/L
1.
2.
0.
0.
1.
2.
0.
1.
2.
3.
4.
0.
1.
1.
260
460
440
800
260
000
950
340
800
600
600"
700
050
000
00610
NH3-N
TOTAL
MG/L
0
0
0
.189
.080
.090
0.072
0
0
0
0
1
1
2
0
0
0
.052
.210
.066
.385
.800
.400
.760
.104
.068
.055
00671 00665
PHOS-DIS PHOS-TOT
ORTHO
MG/L
0.
0.
0.
0.
0.
0.
0.
0.
0.
1.
1.
0.
0.
0.
P
115
058
094
250
084
176
168
360
880
760
900
204
064
060
MG/L P
0.190
0.110
0.150
0.370
0.210
0.330
0.315
0.510
1.250
2.300
2.100
0.270
0.148
0.115
-------
STORET RETRIEVAL DATE 76/04/27
4507G1
34 04 00.0 081 40 30.0 4
BIG CREEK
45 SALUOA CO HWY MA
T/LAKE MURRAY . 030891
ST HWY 450 BRDG .5 MI ABOV L 5 RVR CONFL
11EPALES 2111204
0000 FEET DEPTH CLASS 00
DATE
FROM
TO
73/02/25
73/03/11
73/04/14
73/05/20
73/06/16
73/07/15
73/08/12
73/09/16
73/10/14
73/11/18
73/12/09
74/01/13
74/01/31
74/02/10
00630 00625
TIME DEPTH N02&N03 TOT KJEL
OF N-TOTAL N
DAY FEET MG/L MG/L
13
13
09
13
14
13
09
13
14
10
13
13
10
13
50
40
05
20
10
25
20
20
00
45
55
05
40
40
0.039
0
0
0
0
0
0
0
0
0
0
.130
.088
.088
.100
.017
.010K
.270
.016
o016
0024
0,092
0
0
.140
.176
0
1
0
0
1
3
1
2
1
0
0
•
•
•
•
•
•
•
«
•
•
•
130
000
440
770
150
200
320
700
000
500
800
0.500
0
0
c
•
800
700
00610 00671 00665
NH3-N PHOS-OIS PHOS-TOT
TOTAL ORTHO
MG/L MG/L P MG/L P
0.022
0.046
0.017
0.018
0.044
0.058
0.023
Oo880
Oo056
0.028
0.056
0.044
0.036
0.125
0.015
0.031
0.033
0.024
0.063
0.027
0.022
0.231
0.012
0.016
0.020
0.044
0.056
0.040
0
0
0
0
0
0
0
0
0
0
0
.025
.065
.055
.075
.145
.125
ollO
o375
o!65
«065
.060
0.085
0
0
.110
.080
K VALUE KNOWN TO Bt
LESS THAN INDICATED
-------
STORET RETRIEVAL DATE 76/04/27
4507H1
34 05 00.0 081 38 30.0 4
INDIAN CREEK
45 SALUDA CO HMY MA
T/LAKE MURRAY 030891
ST HWY 90 8RDG .5 MI ABOV MOUTH OF CREEK
11EPALES 2111204
0000 FEET DEPTH CLASS 00
DATE
FROM
TO
73/02/25
73/03/H
73/04/14
73/05/20
73/06/16
73/07/15
73/08/12
73/09/16
73/10/14
73/11/18
73/12/09
74/01/13
74/01/31
74/02/10
00630 00625
TIME DEPTH N02&-N03 TOT KJEL
OF N-TOTAL N
DAY FEET
14
14
09
13
14
13
09
13
14
10
14
13
10
13
10
00
15
30
?0
45
30
35
10
50
05
15
50
50
MG/L
0
0
0
0
0
0
0
0
0
0
0
0
0
0
.252
.350
.270
.035
.210
.063
.150
.230
.062
.010K
.012
.264
.330
.380
MG/L
0.
0.
0.
0.
1.
0.
1.
1.
0.
0.
0.
0.
0.
0.
480
540
390
800
100
720
100
980
250
900
500
300
700
500
00610 00671 00665
NH3-N PHOS-OIS PHOS-TOT
TOTAL ORTHO
MG/L
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
039
016
012
031
054
034
050
094
032
032
016
040
022
MG/L
0.
0.
P
018
048
0.019
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
Oil
074
015
015
078
024
012
012
032
066
045
MG/L P
0.035
0.080
0.050
0.060
0.165
0.060
0.090
0.160
0.090
0.030
0.020
0.055
0.125
0.085
•K VALUE KNOWN TO BE
LESS THAN INDICATED
-------
STORE! RETRIEVAL DATE 76/04/37
4507J1
34 09 30.0 081 37 00.0 4
BUSH RIVER
45 NEWBERRY CO HWY
T/LAKE MURRAY 030891
ST HWY 41 BRDG .5 MI ABOVE MOUTH
11EPALES 2111204
0000 FEET DEPTH CLASS 00
DATE
FROM
TO
73/02/25
73/03/11
73/04/14
73/05/20
73/06/16
73/07/15
73/08/12
73/09/16
73/10/14
73/11/18
73/12/09
74/01/13
74/01/31
74/02/10
00630 00625
TIME DEPTH N02&N03 TOT KJEL
OF N-TOTAL N
DAY FEET
14
14
10
14
14
14
09
14
14
H
14
13
11
14
45
25
15
05
45
10
55
00
40
10
45
3®
30
26
MG/L
0
0
0
1
0
0
1
0
1
0
©
0
0
0
.660
.550
.490
.100
.410
0700
0040
.231
o200
o792
e840
o756
0430
.470
MG/L
0.
1.
0.
0.
1.
0.
0.
Oo
0.
Go
1.
0.
1.
0.
730
680
640
930
540
840
540
940
675
700
800
600
100
800
00610 00671 00665
NH3-N PHOS-DIS PHOS-TOT
TOTAL ORTHO
MG/L
0
0
0
0
0
0
0
0
0
0
.170
.120
.110
.273
.097
.105
.088
o065
.160
0256
0,510
0
0
0
.128
.112
.050
MG/L
0.
0.
0.
0.
0.
P
170
160
147
360
176
0.220
0.
0.
0.
0.
0.
0.
0.
0.
440
140
650
520
330
260
140
115
MG/L P
0.260
0.240
0.230
0.460
Oo440
Oo4JO
Oo575
Oo330
Oo795
Oe630
Oo710
0.390
0«300
0.240
-------
STORET RETRIEVAL DATE 76/04/27
45070A PD4507DA P000800
33 55 32.0 081 28 50.0 4
LEESVILLE
45 LEXINGTON CO HWY
T/LAKE MURRAY 030991
CLOUDS CREEK
11EPALES 2141204
0000 FEET DEPTH CLASS 00
DATE
FROM
TO
73/05/28
73/06/28
73/08/03
73/08/29
73/09/28
73/10/30
73/12/03
74/01/07
74/02/28
74/03/28
74/04/30
7<»/OS/31
74/07/01
00630
TIME DEPTH N02&N03
OF N-TOTAL
DAY FEET
15
14
14
11
14
14
02
14
13
12
11
14
11
00
15
00
00
00
00
45
00
00
00
00
30
00
MG/L
0
0
0
0
0
0
0
0
0
0
0
0
.160
.085
.140
.110
.050
.100
.080
.240
.320
.160
.200
.080
00625
TOT KJEL
N
MG/L
12.000
6.800
16.000
22.000
25.200
22.000
25.000
34.000
12.000
17.000
16.000
18.000
19.000
00610
NH3-N
TOTAL
MG/L
2.900
0.
1.
1.
8.
5.
5.
5.
2.
1.
1.
0.
1.
155
200
340
100
200
700
280
200
600
050
110
000
00671
PHOS-DIS
ORTHO
MG/L
7
5
4
ft
•
ft
P
270
700
700
11.800
11
11
9
7
7
9
8
9
•
ft
ft
ft
ft
ft
ft
ft
000
600
800
200
900
450
900
500
00665 50051 50053
PHOS-TOT FLOW CONDUIT
RATE FLOW-MGD
MG/L P INST MGD MONTHLY
8.250
6.700
9.025
11.500
35.000
13.500
13.500
10.500
8.800
10.500
10.500
11.000 1.000
9.500
-------
STORET RETRIEVAL DATE 76/04/27
4507FA TF4507FA P002500
34 00 05.0 061 45 25.0 4
SALUDA
45 SALUDA CO HWY MP
T/LAKE MURRAY 030892
LITTLE SALUOA RIVER
11EPALES 2141204
0000 FEET DEPTH CLASS 00
DATE
FROM
TO
73/06/15
73/07/12
73/08/20
73/09/18
73/10/05
73/12/15
74/01/07
74/02/06
74/03/11
74/04/07
74/05/10
74/06/10
74/07/08
00630
TIME DEPTH N02&N03
OF N-TOTAL
DAY FEET
14
13
14
13
13
12
14
13
12
16
13
10
14
00
00
30
00
30
00
00
00
30
00
00
00
00
MG/L
0
0
0
0
0
0
0
0
1
0
0
0
0
.370
.560
.052
.400
.190
.120
.640
.120
.040
.720
.320
.680
.760
00625
TOT KJEL
N
MG/L
25.000
29.000
35.000
26.900
36.000
30.000
14.000
19.000
22.000
18.000
33.000
29.000
22.500
00610
NH3-N
TOTAL
MG/L
11.100
10.400
8.700
13.100
11.000
9.050
5.300
7.400
9.200
7.200
14.500
12.500
6.900
00671
PHOS-DIS
ORTHO
MG/L P
6.900
8.600
1.340
10.900
8.200
13.800
6.600
7.400
11.500
7.000
10.500
3.450
6.300
00665
PHOS-TOT
MG/L
11.
12.
17.
15.
16.
9.
10.
12.
8.
13.
10.
10.
50051 50053
FLOW CONDUIT
RATE FLOW-MOD
P INST MGD MONTHLY
000
800
500
700
000
100
000
500
800
500
000
500
0.300
0.300
0.400
0.350
0.300
0.300
0.300
0.300
0.350
0.400
0.350
0.400
0.500
0.300
0.300
0.350
0.350
0.350
0.350
0.350
0.300
0.350
0.350
0.375
0.400
0.500
-------
STORE! RETRIEVAL DATE 76/04/27
4507JA AS4507JA
35 15 50.0 081 38 00.0 4
NEW8ERRY (OCONA)
45 NEWBERRY CO HWY
T/LAKE MURRAY 030891
UNNAMED TRIB/BUSH RIVER
11EPALES 2141204
0000 FEET DEPTH CLASS 00
DATE
FROM
TO
73/06/04
73/06/29
73/07/30
73/08/31
73/09/27
73/10/31
73/11/29
73/12/27
74/01/30
74/02/27
74/03/27
74/04/24
74/05/29
00630
TIME DEPTH N026.N03
OF N-TOTAL
DAY FEET
14
14
15
12
14
11
09
10
10
10
10
09
10
45
15
00
00
30
30
00
30
30
30
15
30
00
00625
TOT KJEL
N
MG/L HG/L
0.
4.
5.
5.
4.
2.
fi.
2.
2.
0.
2.
4.
690
800
100
800
500
200
290
700
800
960
600
500
12.000
6.680
8.500
4.600
8alOO
8.400
I3o000
21.000
10.750
4.900
3.400
9.000
14.000
00610
NH3-N
TOTAL
MG/L
0.138
0.760
0.190
0.330
1.150
Oo670
30400
I0o200
4.800
1.550
0.327
1.150
1.050
00671
PHOS-DIS
ORTHO
MG/L P
3.000
5.500
4.500
12.800
13.000
11.900
15.900
10.400
10.000
10.500
12.500
17.300
16.000
00665
PHOS-TOT
50051 50053
FLOW CONDUIT
RATE FLOW-MOD
MG/L P INST
5.000
6.300
5.950
13.000
13.000
13.600
15.900
11.500
10.000
10.500
14.500
19.000
17.300
0
0
0
0
0
0
0
0
0
0
0
0
0
MGD MONTHLY
o450
.400
.500
.500
o500
o500
.500
.500
.500
.500
.500
.500
.750
0.450
0.400
0.500
OoSOO
OoSOO
OoSOO
OoSOO
OoSOO
OoSOO
0.500
0.500
0.500
0.750
-------
STORET RETRIEVAL DATE 76/04/27
4507JB TF4507JB P010000"
35 15 50.0 081 38 00.0 4
NEWBERRY (SCOTT CHEEK)
45 NEW8ERRY CO H«U
T/LAKE MURRAY 030891
SCOTT CREEK/BUSH RIVEK
11EPALES 2141204
0000 FEET DEPTH CLASS 00
DATE
FROM
TO
73/06/04
CP < T > -
73/06/04
73/06/29
CP(T>-
73/06/29
73/07/30
CP-
73/07/30
73/08/31
CP(T)-
73/08/31
73/09/27
CP-
73/09/27
73/10/30
CP(T>-
73/10/30
73/11/30
CP(T)-
73/11/30
73/12/28
CP(T>-
73/12/28
74/01/31
CP < T > -
74/01/31
74/02/28
CP(T>-
74/02/28
74/03/28
CP(T)-
74/03/28
74/04/23
CP(T)-
74/04/24
00630
TIME DEPTH N02&N03
OF N-TOTAL
DAY FEET MG/L
08
16
09
16
09
16
08
15
08
15
09
16
08
15
09
16
09
16
09
16
U9
16
14
14
30
30
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
30
30
0
0
0
0
0
0
0
0
0
0
0
0
.250
.240
.520
.220
.154
.210
.200
.200
.240
.400
.400
.160
00625
TOT KJEL
N
MG/L
23.100
23.100
27.300
30.500
24.900
31.000
33.000
27.000
15.000
19.500
23.500
22.000
00610 00671
NH3-N PHOS-DIS
TOTAL ORTHO
MG/L MG/L P
10.000
10.000
15.800
12.250
16.000
13.000
14.000
10.200
5.800
8.600
9.600
8.600
5.800
7.300
7.000
6.900
8.600
7.100
7.100
a. 500
4.600
6.700
6.400
8.000
00665 50051 50053
PHOS-TOT FLO* CONDUIT
RATE FLOW-MOD
MG/L P INST MGD MONTHLY
10
10
12
11
8
8
9
12
9
9
9
11
.000
.000
.500
.000
.700
.400
.700
.000
.100
.000
.950
.500
1.200
1.100
0.825
1.000
1.200
1.150
1.000
1.020
1.600
1.250
1.100
1.100
1.030
1.300
0.892
1.100
1.260
1.030
1.040
1.090
1.460
1.410
1.130
1.150
-------
STORE! RETRIEVAL DATE 76/04/27
00630
DATE TIME DEPTH N02&N03
FROM OF N°TOTAL
TO DAY FEET MG/L
74/05/31 08 00
CP(T)-
74/05/31 16 00
4507JB TF4507J8 P010000*
35 15 50.0 081 38 00.0 4
NEWBERRY (SCOTT CREEK)
45 NEHBERRY CO HWY
T/LAKE MURRAY 030891
SCOTT CREEK/BUSH RIVER
11EPALES 2141204
0000 FEET DEPTH CLASS 00
00625
TOT KJEL
N
MG/L
00610
NH3-N
TOTAL
MG/L
00671
PHOS-DIS
ORTHO
MG/L P
00665
PHOS-TOT
MG/L P
50051
FLOk)
RATE
INST MGD
50053
CONDUIT
FLOuHMGD
MONTHLY
Ool68
340000
12o500
8.600
13oOOO
loOOO
loOSO
-------
STORE! RETRIEVAL DATE 76/04/27
4507JC PD4507JC P000160*
35 15 50.0 081 38 00.0 4
NEWBERRY (GREEN SPRING)
45 NEWBERRY CO HWf
T/LAKE MURRAY 030891
GREEN SPRING CREEK/BUSH RIVER
11EPALES 2141204
0000 FEET DEPTH CLASS 00
DATE
FROM
TO
73/06/04
73/06/28
73/07/30
73/08/31
73/09/27
73/10/31
73/11/29
73/12/27
74/01/30
74/02/27
74/03/27
74/04/24
74/05/29
00630 00625
TIME DEPTH N02&N03 TOT KJEL
OF N-TOTAL N
DAY FEET
14
14
15
11
14
11
08
09
09
09
09
09
09
15
30
30
30
00
00
30
45
30
30
45
00
30
MG/L
0
0
0
0
0
0
C
0
0
0
.010*
.060
.060
.220
.070
.070
.130
.160
.240
.160
0.040
0
.120
MG/L
2.500
3.700
4.600
5.900
6.440
2.500
3.500
4.300
3.000
2.900
1.600
3.500
6.000
00610 00671 00665
NH3-N PHOS-DIS PHOS-TOT
TOTAL ORTHO
MG/L
0.073
0.200
0.170
0.620
0.692
0.130
0.110
0.420
0.480
0.600
0.150
0.100
0.050K
MG/L P
0.115
0.190
0.073
0.078
0.340
0.130
0.083
0.200
0.100
0.100
0.210
0.190
50051 50053
FLOW CONDUIT
RATE FLOW-MGD
MG/L P INST
0.210
0.200
0.266
0.235
0.645
0.190
0.280
0.150
0.270
0.290
0.300
0.225
0
0
0
0
0
0
0
0
0
0
0
0
0
MGO MONTHLY
.003
.003
.003
.003
.003
o003
o003
o003
o003
.003
.003
.003
.004
0.003
0.003
0.003
0.003
0.003
0.003
0.003
Oo003
0.003
0.003
0.003
0.003
0.004
K VALUE KNOWN TO BE
LESS THAN INDICATED
-------
STORET RETRIEVAL DATE 76/04/27
4507JD PD4507JD P001000<
35 15 50.0 081 38 00.0 4
NEWBERRY (POOL #1)
45 NEWBERRY CO HrfY
T/LAKE MURRAY 030891
UNNAMED CREEK/BUSH RIVER
11EPALES 2141204
0000 FEET DEPTH CLASS 00
DATE
FROM
TO
73/06/04
73/06/29
73/07/30
73/08/31
73/09/27
73/10/31
73/11/29
73/12/27
74/01/30
74/02/27
74/03/27
74/04/24
74/05/29
00630
TIME DEPTH N02&N03
OF N-TOTAL
DAY FEET
14
14
15
11
14
10
09
11
11
11
10
10
10
30
45
15
45
15
00
45
00
30
00
45
00
30
MG/L
0
0
0
0
0
0
0
0
0
0
0
.013
.040
.040
.090
.040
.050
.080
.040
.080
.120
.040
00625
TOT KJEL
N
MG/L
0.920
5.740
8.800
8.500
10.500
9.100
15.000
10.500
13.000
8.600
7.400
15.000
00610 00671 00665
NH3-N PHOS-DIS PHOS-TOT
TOTAL ORTHO
MG/L
0.052
0.150
0.145
0.057
0.300
0.110
0.100
0.340
0.100
0.100
0.450
0.063
MG/L P
1.200
1.100
1.700
2.660
2.600
2.300
2.400
2.100
1.480
0.970
1.400
1.700
50051 50053
FLOW CONDUIT
RATE FLOW-MOD
MG/L P INST
1.650
1.950
3.400
3.700
4.000
3.600
5.250
4.000
6.100
3.600
3.600
4.200
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
MGD MONTHLY
150
150
150
150
150
150
150
150
150
150
150
150
150
0.150
0.150
0.150
0.150
0.150
0.150
0.150
0.150
0.150
0.150
-------
STORET RETRIEVAL DATE 76/04/27
4507XA PD4507XA P000500
35 13 00.0 081 33 30.0 4
PROSPERITY *1
45 NEWBERRY CO HWY
T/LAKE MURRAY 030891
TIMOTHY CREEK - Sk» LAGOON
11EPALES 2141204
0000 FEET DEPTH CLASS 00
DATE
FROM
TO
73/05/30
73/07/03
73/07/31
73/08/28
73/10/02
73/10/30
73/11/27
73/12/31
74/01/31
74/02/28
74/03/29
74/05/08
74/05/30
00630
TIME DEPTH N02&N03
OF N-TOTAL
DAY FEET
10
10
10
09
09
09
10
09
10
iO
11
11
09
30
15
00
45
30
30
15
45
15
10
30
40
36
MG/L
4
23
16
24
23
24
7
20
22
17
13
11
.200
.000
.400
.000
.000
.000
o500
oOOO
oOOO
o600
.000
.000
00625
TOT KJEL
N
MG/L
23.100
7.000
6.200
8.200
13.000
14.000
17.000
45.000
22.000
10.000
9.400
24.000
34.000
00610
NH3-N
TOTAL
MG/L
8.300
0.350
0.100
0.110
0.270
0.220
Oo240
16,000
Oo420
0.910
Oo430
8.200
14.000
00671
PHOS-DIS
ORTHO
MG/L P
10.000
9.900
10.600
14.000
13.700
15.800
14.700
15»000
13.000
9.100
12.500
15.700
14.700
00665
PHOS-TOT
50051 50053
FLOW CONDUIT
RATE FLOW-MOD
MG/L P INST
15.700
11.500
14.500
17oOOO
160000
15o80®
180800
18oOOO
16o509
13o500
17eOOO
18oOOO
16.250
0
0
0
0
0
0
0
0
0
0
0
0
0
MGO MONTHLY
.040
.020
.030
*030
°030
o030
o030
o030
o030
»030
o025
.030
.025
0.025
0.025
0.025
0.025
Oc025
Oo025
Oo025
00025
00080
0.020
0.025
0.025
-------
STORET RETRIEVAL DATE 76/04/27
4507X8 AP4507XB P000300
34 13 00.0 081 33 31.0 4
PROSPERITY *2 (NORTHWEST LAGOON)
45 NEWBERRY CO HWY
T/LAKE MURRAY 030891
TIMOTHY CREEK - NE LAGOON
11EPALES 2141204
0000 FEET DEPTH CLASS 00
DATE
FROM
TO
73/05/30
73/07/03
73/07/31
73/08/28
73/10/02
73/10/30
73/11/27
73/12/31
74/01/31
74/02/28
74/03/29
74/05/08
74/05/30
00630
TIME DEPTH N02&N03
OF N-TOTAL
DAY FEET
11
10
10
09
10
10
10
09
09
09
11
11
09
00
45
30
15
00
25
40
25
45
30
15
25
05
MG/L
0.
0.
0.
0.
0.
0.
0.
1.
0.
0.
0.
0.
0.
130
390
150
690
130
200
230
200
200
280
200
600
320
00625
TOT KJEL
N
MG/L
29.400
23.100
18.900
38.250
18.900
27.000
39.000
32.500
26.000
20.000
24.000
38.000
20.000
00610
NH3-N
TOTAL
MG/L
3.100
0.980
3.800
5.110
0.250
5.600
8.400
8.800
6.900
5.800
6.000
5.880
0.320
00671
PHOS-DIS
ORTHO
MG/L P
9.200
8.600
1.850
22.250
26.500
24.000
26.000
25.000
19.000
18.000
17.000
19.500
20.000
00665
PHOS-TOT
50051 50053
FLOW CONDUIT
RATE FLOW-MOD
MG/L P INST
23.000
23.000
25.000
31.500
27.150
38.500
29.000
28.800
20.000
20.000
22.000
25.000
23.000
0
0
0
0
0
0
0
0
0
0
0
0
0
MGD MONTHLY
.020
.035
.045
.045
.045
.045
.045
.045
.045
.045
.045
.045
.045
0.040
0.040
0.040
0.040
0.040
0.040
0.040
0.040
0.040
0.040
0.040
0.040
-------
STORET RETRIEVAL DATE 76/04/27
DATE
FROM
TO
73/06/01
73/07/03
73/08/03
73/09/05
73/10/02
73/11/05
73/12/04
74/01/09
74/02/11
74/03/06
74/04/01
74/05/07
00630
TIME DEPTH N02&N03
OF N-TOTAL
DAY FEET MG/L
11 00
10 00
14 00
14 00
15 00
14 30
13 00
14 00
13 30
10 30
13 30
14 00
0.320
2.300
1.400
4.440
6.700
3.000
2.900
1.320
1.560
2.240
2.320
4507ZA TF4507ZA P002500
33 53 10.0 081 33 10.0 4
BATESBURG (DUNCAN CREEK)
45 LEXINGTON CO MAP
T/LAKE MURRAY 030892
DUNCAN CREEK
11EPALES
2141204
0000 FEET DEPTH CLASS 00
00625
TOT KJEL
N
MG/L
12.000
6.300
12.000
13.000
13.500
15.000
9.600
6.100
9.000
13.000
00610
NH3-N
TOTAL
MG/L
4.900
3.100
4.800
5.500
6.800
5.600
4.200
2.500
6.100
5.600
00671
PHOS-OIS
ORTHO
MG/L P
4.200
1.250
3.900
2.200
9.000
8.300
5.280
1.650
3.900
4.400
00665
PHOS-TOT
MG/L P
5.200
2.000
5.800
10.000
10.500
10.500
6.900
2.300
6.600
6.100
50051
FLOW
RATE
INST MGD
0.300
0.405
0.405
0.400
0.350
0.405
0.400
0.395
0.375
0.375
50053
CONDUIT
FLOW-MOD
MONTHLY
0.330
0.400
0.405
0.405
0.400
0.405
-------
STORE! RETRIEVAL DATE 76/04/27
4507YA TF4507YA P002500
33 55 22.0 081 33 25.0 4
BATESBURG (WEST CREEK)
45 SALUDA CO HWY MP
T/LAKE MURRAY 030892
WEST CREEK
11EPALES
2141204
0000 FEET DEPTH CLASS 00
DATE
FROM
TO
73/06/01
73/07/03
73/08/03
73/09/05
73/10/02
73/11/05
73/12/04
74/01/09
74/02/11
74/C3/06
74/04/01
74/05/07
TIME DEPTH
OF
DAY FEET
11 30
10 30
14 30
13 30
14 00
14 00
13 30
13 30
13 00
11 00
13 45
14 30
00630
N02&N03
N-TOTAL
MG/L
1.000
0.520
0.230
0.048
0.130
0.370
0.420
0.640
2.000
1.240
1.000
00625
TOT KJEL
N
MG/L
24.000
9.600
40.000
24.000
37.500
35.000
54.000
38.000
42.000
42.000
00610
NH3-N
TOTAL
MG/L
5.690
3.900
9.300
9.100
4.000
3.400
10.100
6.500
17.300
6.100
00671
PHOS-DIS
ORTHO
MG/L P
6.600
1.860
4.300
2.400
5.500
4.700
4.300
4.300
10.000
5.900
00665
PHOS-TOT
MG/L P
16.000
3.200
8.450
3.400
12.000
10.500
6.950
7.050
14.500
9.600
50051
FLOW
RATE
INST MOD
0.300
0.230
0.230
0.230
0.200
0.230
0.200
0.200
0.225
0.200
50053
CONDUIT
FLOW-MGD
MONTHLY
0.400
0.300
0.230
0.230
0.230
0.230
------- |