U.S. ENVIRONMENTAL PROTECTION AGENCY
NATIONAL EUTROPHICATION SURVEY
WORKING PAPER SERIES
REPORT
ON
WEISS RESERVOIR
CHEROKEE COUNTY, ALABAm
AND
FLOYD COUNTY, GEORGIA
EPA REGION IV
WORKING PAPER No, 235
CORVALLIS ENVIRONMENTAL RESEARCH LABORATORY - CORVALLIS, OREGON
and
ENVIRONMENTAL MONITORING & SUPPORT LABORATORY - LAS VEGAS, NEVADA
•&G.P.O. 699-440
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REPORT
ON
WEISS RESERVOIR
CHEROKEE COUNTY, ALABAMA
AND
FLOYD COUNTY, GEORGIA
EPA REGION IV
WORKING PAPER No, 235
WITH THE COOPERATION OF THE
ALABAMA WATER IMPROVEMENT COMMISSION
AND THE
ALABAMA NATIONAL GUARD
JULY 1976
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CONTENTS
Foreword i i
List of Study Lakes - Alabama 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 13
V. Literature Reviewed 20
VI. Appendices 21
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ii
FOREWORD
The National Eutrophicaflon 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, concen-
trations, 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 nonpoint source pollution abatement in lake water-
sheds.
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
watershed 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)L water quality criteria/standards review
L§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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TM
Beyond the single lake analysis, broader based correlations
between nutrient concentrations (and loading) and trophic condition
are being made to advance the rationale and data base for refine-
ment 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 the U.S. Environmental Protection
Agency and to augment plans implementation by the states.
ACKNOWLEDGEMENTS
The staff of the National Eutrophication Survey (Office of
Research and Development, U.S. Environmental Protection Agency)
expresses sincere appreciation to the Alabama Water Improvement
Commission for professional involvement and to the Alabama National
Guard for conducting the tributary sampling phase of the Survey.
E. John WiHi ford, Chief, Surveillance and Monitoring Section;
and John C. Chitwood, Biologist, Surveillance and Monitoring Section;
and Sam L. Coleman, Water Quality Planning Section; and M. H. Floyd,
Engineer, Surveillance and Monitoring Section; and Truman Green,
Engineer, Municipal Waste Control Section; and Tim McCartha, Biologist,
Surveillance and Monitoring Section; and James E. Mclndoe, Engineer,
Water Quality Planning Section; and Richard T. Maddox, Engineer,
Industrial Waste Control Section; and James T. White, Engineer,
Municipal Waste Control Section provided invaluable lake docu-
mentation and counsel during the course of the Survey.
Major General Charles A. Rollo, Adjutant General of Alabama,
and Project Officer Lt. Col. Wash B. Ray, who directed the volun-
teer efforts of the Alabama National Guardsmen, are also gratefully
acknowledged for their assistance to the Survey.
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IV
NATIONAL EUTROPHICATION SURVEY
STUDY LAKES
STATE OF ALABAMA
LAKE NAME
Bankhead
Gantt
Guntersville
Holt Lock and Dam
Lay
Martin
Mitchell
Pickwick
Purdy
Weiss
Wilson
COUNTY
Walker
Covington
Marshall, Johnson
Tuscaloosa
Chi 1 ton, Coosa
Elmore, Tallapoosa
Coosa, Chi 1 ton
Colbert, Lauderdale
(Tishomingo in MS
and Hardin in TN)
Jefferson, Shelby
Cherokee
Lauderdale, Colbert,
Lawrence
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WEISS
RESERVOIR
Tributary Sampling Site
Lake Sampling Site
Sewage Treatment Facility
Drainage-Area Boundary
10 20 m Km
Mi
5 10
>
f 34* 45'-
WEISS
KESERVOIR
°°"' }—BA
'eservoir \ \
ALA.) GA.
Map Location
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WEISS RESERVOIR, ALABAMA AND GEORGIA
STORE! NO. 0112
I. CONCLUSIONS
A. Trophic Condition:*
Weiss Reservoir is classified as eutrophic based
upon Survey data, i.e., nutrient rich and highly
productive. Whether such nutrient enrichment is to
be considered beneficial or deleterious is determined
by its actual or potential impact upon designated
beneficial water uses of each lake.
Of the 11 Alabama lakes surveyed in 1973, none
had higher median total phosphorus and chlorophyll a_
values or lower Secchi disc transparency than this
Coosa River impoundment. Marked depression of dissolved
oxygen with depth occurred at Station 4 during June and
August. The phytoplankton was dominated by large numbers
of pollution-tolerant genera, and field limnologists
reported abundant emergent vegetation along shoreline
areas of the reservoir.
B. Rate-Limiting Nutrient:
Algal assay results suggest that Weiss Reservoir
was colimited by nitrogen and phosphorus in primary
production at Stations 1 through 4 and limited by available
*See Appendix E.
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nitrogen levels at Stations 5 and 6. The ratios of inor-
ganic nitrogen to orthophosphorus (N/P) in sampled waters
were generally consistent with nitrogen limitation.
Nutrient Controllability:
1. Point sources -
The mean annual phosphorus load from point sources
was estimated to be 22.1% of the total load reaching
Weiss Reservoir. The city of Calhoun, Georgia, con-
tributed a total of 9.6%, and Rome, Georgia, contributed
8.3%. The remaining five known wastewater treatment
plants contributed a total of 4.2% of the total load.
The present loading of 9.45 g P/m^/yr is about 6
times that proposed by Vollenweider (1975) as eutrophic,
and 12 times the proposed oligotrophic load. However,
Vollenweider's model may not be applicable to lakes with
short hydraulic retention times, and the retention time
Of Weiss Reservoir is only 16 days.
2. Nonpoint sources -
The mean annual phosphorus load from nonpoint sources
was about 77.9% of the load reaching Weiss Reservoir. The
Coosa River system accounted for 73.1% of this nonpoint
contribution, and ungaged drainage areas were estimated to
have contributed 0.9%. Nutrient contributions from the
cities of Cartersville and Dalton were not included in the
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nutrient budget for Weiss Reservoir due to their distance
from the Coosa River inlet sampling station. It is ex-
pected, however, that the unusually high background
loading for the Coosa River is due, at least in part,
to unmeasured contributions from these areas.
In general, few lakes are nitrogen limited as a
result of low nitrogen. Rather, excessive phosphorus
levels shift limitations to nitrogen or other factors.
Regardless of the primary nutrient limitation suggested
by either algal assay or nutrient ratios, the most feasi-
ble approach to nutrient control, if desirable, is through
available phosphorus control technology and subsequent
establishment of phosphorus limitation within the water
body.
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II. LAKE AND DRAINAGE BASIN CHARACTERISTICS
Lake and drainage basin characteristics are itemized
below. Lake surface area and mean depth were provided by
the Alabama Water Improvement Commission; maximum depth
was estimated on the basis of National Eutrophication
Survey (NES) sampling data; tributary flow data were
provided by the Alabama District Office of the U.S. Geological
Survey (USGS)(outlet drainage area includes the lake surface
area). Mean hydraulic retention time was obtained by dividing
the lake volume by mean flow of the outlet. Precipitation
values were estimated by methods as outlined in NES Working
Paper No. 175. A table of metric/English conversions is
included as Appendix A.
A. Lake Morphometry:
1. Surface area: 122.22 km2.
2. Mean depth: 2.8 meters.
3. Maximum depth: 15.2 meters.
4. Volume: 342.216 x 106 m3.
5. Mean hydraulic retention time: 16 days.
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B. Tributary and Outlet (see Appendix B for flow data):
1. Tributaries -
Drainage Mean flow
Name area(km2) (m3/sec)
A(l) Coosa River 10,650.1 185.23
B(l) Mt. Hope Creek 22.8 0.37
C(l) King Creek 26.9 0.46
D(l) Big Cedar Creek 510.2 8.00
E(l) Mud Creek 23.8 0.39
F(l) Spring Creek (south) 110.1 1.27
6(1) Yellow Creek 80.3 2.01
H(l) Little River . 502.5 12.78
J(l) Spring Creek (north) 94.5 2.59
K(l) Chattooga River 976.4 18.34
Minor tributaries and
immediate drainage - 530.5 . 12.04
Totals 13,528.1 243.48
2. Outlet - Coosa River 13,649.3 252.56
C. Precipitation:
1. Year of sampling: 176.0 cm.
2. Mean annual: 136.4 cm.
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III. LAKE WATER QUALITY SUMMARY
Weiss Reservoir was sampled four times during the open-
water season of 1973 by means of a pontoon-equipped Huey
.helicopter. Each time, samples for physical and chemical
parameters were collected from six stations on the lake
(one station was sampled four times, four stations were
sampled three times, and one station was sampled twice) and
from one or more depths at each station (see map). During
each visit, depth-integrated samples were collected from each
-station for chlorophyll ^analysis and phytoplankton identi-
fication and enumeration. During the first visit, 18.9-liter
depth-integrated samples were composited for algal assays.
Maximum depths sampled were 9.0 m at Station 1, 14.0 m at
Station 2, 11.0 m at Station 3, 7.6 m at Station 4, 9.1 m at
Station 5, and 9.1 m at Station 6. For a more detailed
explanation of NES methods, see NES Working Paper No. 175.
The results obtained are presented in full in Appendix C
and are summarized in III-A for waters at the surface and at
the maximum depth for each site. Results of the phytoplankton
counts and chlorophyll a_ determinations are included in III-B.
Results of the limiting nutrient study are presented in III-C.
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WEISS RESEWVDIR
STORET CODE oil?
PARAMETER
TEMPERATURE
0.-1.5 M UEPTH 1
MAX DEPTH" 1
TOTAL P (MG/L)
O.-l. 3 M DEPTH
MAX DEPTH""
1
1
DISSOLVED ORTHO P (MG/L)
O.-l. 5 M DEPTH 1
MAX UEP1H"" 1
NU3»N01 (M'i/L)
O.-l. 5 M DEPTH
MAX DEPTH""
AMMONIA (MO/LI '
O.-l. 5 .1 DE"TH
MAX DEPTH""
KJELDAHL N (MG/L)
O.-l. 5 M DEPTH
MAX DEPTH"
SFCCrtl DISC (METERS)
1
1
1
1
1
,
( 3/19/73 )
S««» = 1
RANGE MEDIAN
14.4- 14.4
l
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WEISS RESF.P.V01R
STOflET CODE 0112
PAHAMETEK
TEMPEKATUWE (DEC,
O.-l.S M DEPTH
MAX DEPTH"
DISSOLVED OXYGEN
O.-l.b M DEPTH
MAX DEPTH**
( 10/30/73 )
S"* = 5
N* RANGE MEDIAN
CENT)
7
5
(MG/L)
3
5
CONDUCTIVITY (UMHOS)
O.-l .b M UEPT4 7
MAX OEPTH" 5
PH (STANDARD UNITS)
0.-I.5 "1 DEPTH 7
MAX DEPTH** S
TOTAL ALKALINITY
0.-1.5 H DEPTH
MAX DEPTH**
TOTAL P (MG/L)
O.-l.S M DEPTH
MAX DEPTH**
DISSOLVED OKTHO P
o.-i.s M OE»TH
MAX DEPTH"
N02»M03 (MG/L>
0.-1.5 M DEPTH
MAX DEPTH**
AMMONIA (MG/L)
li.-l .'-j M DEPTH
MAX OtPIH"
KjELOuHL N (MG/L)
O.-l.S « DEPTH
MAX DEPTH**
(MG/L)
7
S
7
5
(MG/L)
7
S
7
S
7
5
7
5
16.0-
15.9-
6.9-
7.2-
103.-
103.-
7.2-
7.1-
45.-
45.-
17.8
17.7
8.2
8.2
204.
203.
7.8
7.9
97.
98.
0.074-0.137
O.OB4-0.150
0.042-0.077
0.0-41-0.077
O.ObO-0
0.040-0
O.ObO-0
0.060-0
0.400-0
0.400-0
.160
.150
.140
.14C
.500
.700
17. b
16.0
7.2
7.8
114.
113.
7.3
7.5
50.
50.
0.097
0.117
0.044
0.045
0.110
0.100
0.1?0
0.110
0.500
0.400
p
HI
MAX
DEPTH
P.ANC3E
(METEP.S)
0
0
0
0
0
0
0
c
0
0
0
0
0
0
0
0
0
0
0
0
.0-
.0-
.0-
.0-
.0-
.0-
.0-
.0-
.0-
.0-
.0-
.0-
.0-
.0-
.0-
.0-
.0-
.0-
.0-
.0-
1.
12.
1.
12.
5
8
5
a
l.S
12.3
1.
12.
1.
12.
1.
12.
1.
12.
1.
12.
1.
12.
1.
12.
5
8
5
B
5
8
5
8
S
8
5
5
8
PHYSICAL AND CHEMICAL CHAKACTEKISTICS
SECCHI DISC (METERS)
0.3- 0.9
* rj = Mi). OF SAMPLES
«» MAXIMUM DEPTH SAMPLED AT EACH SITE
«*« S = NO. OF SITES SAMPLED ON THIS DATE
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B. Biological Characteristics:
1. Phytoplankton -
Sampling
Date
03/19/73
08/25/73
10/30/73
Dominant
Genera
1. Melosira
2. Synedra
3. Dinobryon
4. Cyclotella
5. Cryptomonas
Other genera
Total
1. Melosira
2. Flagellates
3. Oscillatoria
4. Cyclotella
5. Lyngbya
Other genera
Total
1. Melosira
2. Cyclotella
3. Flagellates
4. Dactylococcopsis
5. Synedra
Other genera
Total
Algal
Units
per ml
1,029
250
209
181
125
515
2,309
3,829
1,650
1,585
858
792
3,500
12,214
6,072
1,291
1,291
1,252
607
1.935
12,448
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10
2. Chlorophyll a_ -
Sampling Station Chlorophyll a_
Date Number (yg/liter)
03/19/73 1 3.6
06/08/73 1 6.9
2 8.4
3 10.8
4 6.5
5 9.4
6 6.7
08/25/73 1 9.7
2 21.4
3 22.0
4 18.8
5 12.6
6 3.7
10/30/73 1 4.1
2 6.0
3 9.8
4 25.2
5
6 17.1
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11
C. Limiting Nutrient Study:
1. Stations 1 through 4 -
a. Autoclaved, filtered, and nutrient spiked
Spike(mg/l)
Control
0.010
0.020
0.050
0.025
0.050
1.0 N
P
P
P
P +
P +
0.5
1.0
Ortho P
Cone.(mg/1)
0.020
0.030
0.040
0.070
0.045
0.070
0.020
Inorganic N
Cone.(mg/1)
0.
0.
0.
0.
0.
1.
178
178
178
178
678
178
1.178
Maximum Yield
(mg/1-dry wt.)
5.7
7.3
6.6
7.7
16.3
28.0
8.5
b. Filtered and nutrient spiked
Spike(mg/l)
Control
0.010 P
0.020 P
0.050 P
0.025 P
0.050 P
1.0 N
+ 0.5 N
+ 1.0 N
Ortho P
Cone.(mg/1)
0.018
0.028
0.038
0.068
0.043
0.068
0.018
Inorganic N
Cone.(mg/1)
0.205
0.205
0.205
0.205
0.705
1.205
1.205
Maximum Yield
(mg/1-dry wt.)
4.9
5.6
5.6
5.6
12.5
29.0
6.1
2. Stations 5 and 6 -
a. Autoclaved, filtered, and nutrient spiked
Spike(mg/l)
Control
0.010 P
0.020 P
0.050 P
0.025 P +
0.050 P +
1.0 N
0.5 N
1.0 N
Ortho P
Cone.(mg/1)
0.044
0.054
0.064
0.094'
0.069
0.094
0.044
Inorganic N
Cone.(mg/1)
0.262
0.262
0.262
0.262
0.762
1.262
1.262
Maximum Yield
(mg/1-dry wt.)
6.2
5.9
5.5
7.8
16.6
26.9
13.4
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Ortho P
Cone. (mg/1 )
0.028
0.038
0.048
0.078
0.053
0.078
0.028
Inorganic N
Cone. (mg/1)
0.241
0.241
0.241
0.241
0.741
1.241
1.241
Maximum Yield
(mg/1 -dry wt.)
4.5
4.5
4.7
4.4
10.7
19.0
9.7
12
b. Filtered and nutrient spiked
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 results of the algal assays with Selenastrum
capricornutum indicate that potential primary production
was high in Weiss Reservoir at the time of sample analyses.
In the Stations 1 through 4 sample, additions of either
phosphorus or nitrogen alone resulted in moderate increases
in yield, suggesting primary col imitation by the two
nutrients. In the Stations 5 and 6 sample, increases in
yield with the addition of nitrogen as well as a lack of
response when only phosphorus was added indicate nitrogen
limitation. In all samples, maximum growth potentials were
achieved with the simultaneous addition of both phosphorus
and nitrogen.
The N/P ratios in the field samples for Weiss Reservoir
were 11/1 or less indicating the lake was nitrogen limited at
all sampling periods (i.e., an N/P ratio of 14/1 or greater
generally reflects phosphorus limitation).
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13
IV. NUTRIENT LOADINGS
(See Appendix D for data)
For the determination of nutrient loadings, the Alabama
National Guard collected monthly near-surface grab samples
from each of the tributary sites indicated (see map), except
for the high runoff months of January and February when two
samples were collected. Sampling was begun in March 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 Alabama District Office of USGS for the
tributary sites nearest the lake.
In this report, nutrient loads for sampled tributaries*
were determined by using a modification of a USGS computer
program for calculating stream loadings. Nutrient loads
indicated for tributaries are those measured minus known
point source loads, if any.
Nutrient loadings for Big Cedar Creek, the .Chattooga
River, and the unsampled "minor tributaries and immediate
drainage" ("ZZ" of USGS) were estimated by using the mean
annual nutrient loads, in kg/km2/yr, at Stations B(l), C(l),
G(l), H(l), and J(l), and multiplying the means by the
appropriate area in km2.
*With the exception of Big Cedar Creek and the Chattooga
River, Stations D(l) and K(l).
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14
The operators of the Rome, Cedartown, Burgess Manufacturing,
Calhoun, Trion (all in Georgia), and Summerville wastewater treat-
ment plants provided monthly effluent samples and corresponding
flow data. Nutrient loads for the Cave Springs wastewater treatment
plant were estimated at 1.134 kg P and 3.401 kg N/capita/yr.
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15
A. Waste Sources:
1. Known municipal -
Name
Rome (Georgia)
Cedartown (Georgia)
Cave Springs
Burgess Manufacturing
(Georgia)
Summervillet
Trion (Georgia)
Calhoun (Georgia)
Population
Served
60,000
7,000
1,305*
150
4,000
50,500
70,000
Treatment
1.
1.
2.
3.
2.
2.
1.
Mean Flow
(m3/d x 103)
25.893
3.696
0.494**
0.038
4.164
15.659
22.488
Receiving
Water
Coosa River
Big Cedar Creek
Cedar Creek
Chattooga River
Mt. Hope Creek
Chattooga River
Oostanaula River
Key: 1. Trickling filter
2. Activated sludge
3. Stabilization pond
*1970 Census.
**Estimated at 0.3785 m3/capita/day.
tPlant receives 50% industrial waste (carpet mill).
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16
B. Annual Total Phosphorus Loading - Average Year:
1. Inputs -
% of
Source kg P/yr total
a. Tributaries (nonpoint load) -
A(l) Coosa River ' 844,420 73.1
B(l) Mt. Hope Creek 280 <0.1
C(l) King Creek 165 <0.1
D(l) Big Cedar Creek 9,695 0.8
E(l) Mud Creek 370 <0.1
F(l) Spring Creek (south) 1,390 0.1
G(l) Yellow Creek 2,400 0.2
H(l) Little River 8,215 0.7
J(l) Spring Creek (north) 2,850 0.3
K(l) Chattooga River 18,550 1.6
b. Minor tributaries and immediate
drainage (nonpoint load) - 10,080 0.9
c. Known municipal STP's -
Rome (Georgia) 96,135 8.3
Cedartown (Georgia) 8,915 0.8
Cave Springs 1,480 O.'l
Burgess Manufacturing 50 <0.1
Summerville 19,345 1.7
Trion (Georgia) 18,160 1.6
Calhoun (Georgia) 110,505 9.6
d. Septic tanks* - 130 <0.1
e. Known industrial** - None
f. Direct precipitationt - 2.140 0.2
Totals 1,155,275 100.0
2. Output - Coosa River 706,815
3. Net annual P accumulation - 448,460
*Estimate based on 465 lakeshore residences.
**See t footnote, page 14.
tEstimated (see NES Working Paper No. 175).
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17
C. Annual Total Nitrogen Loading - Average Year:
1. Inputs -
Source kg N/yr.
a. Tributaries (nonpoint load) -
A(l) Coosa River 6,456,340 73.6
B(l) Mt. Hope Creek 9,820 0.1
C(l) King Creek 9,315 0.1
0(1) Big Cedar Creek 314,795 3.6
E(l) Mud Creek 13,855 0.1
F(l) Spring Creek (south) 48,360 0.5
6(1) Yellow Creek 73,845 0.8
H(l) Little River 377,140 4.3
J(l) Spring Creek (north) 60,405 0.7
K(l) Chattooga River 602,440 6.9
b. Minor tributaries and immediate
drainage (nonpoint load) - 327,320 3.7
c. Known municipal STP's -
Rome (Georgia) 118,265 1.3
Cedartown (Georgia) 9,445 0.1
Cave Springs 4,440 0.1
Burgess Manufacturing 525 <0.1
Summerville 9,560 0.1
Trion (Georgia) 111,160 1.3
Calhoun (Georgia) 83,860 1.0
d. Septic tanks* - 4,955 1.0
e. Known industrial** - None
f. Direct precipitationt - 131.950 1.5
Totals 8,767,795 100.0
2. Output - Coosa River 5,920,780
3. Net annual N accumulation - . 2,847,015
*Estimate based on 465 lakeshore residences
**See t footnote, page 14.
tEstimated (see NES Working Paper No. 175).
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18
D. Mean Annual Nonpoint Nutrient Export by Subdrainage Area:
Tributary kg P/km?/yr kg N/km?/yr
Coosa River 79* 606
Mt. Hope Creek 12 430
King Creek 6 346
Big Cedar Creek ' 19 617
Mud Creek 16 582
Spring Creek (south) 13 439
Yellow Creek 30 920
Little River 16 750
Spring Creek (north) 30 639
Chattooga River 19 617
*Background phosphorus level for this river probably inflated
by unmeasured point sources upstream (see discussion, page 3)
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19
F. Yearly Loadings:
In the following table, the existing phosphorus annual
loading is compared to the relationship proposed by Vollenweider
(1975). Essentially, his eutrophic loading is that at which
the receiving waters would become eutrophic or remain eutrophic;
his oligotrophic loading is that which would result in the
receiving water remaining oligotrophic or becoming oligotrophic
if morphometry permitted. A mesotrophic loading would be
considered one between eutrophic and oligotrophic.
Note that Vollenweider's model may not apply to lakes with
short hydraulic retention times or in which light penetration is
severely restricted by high concentrations of suspended solids
in the surface waters.
Total Yearly
Phosphorus Loading
(g/m2/yr)
Estimated loading for Weiss Reservoir 9.45
Vollenweider's eutrophic loading 1.53
Vollenweider's oligotrophic loading 0.76
-------
20
V. LITERATURE REVIEWED
U.S. Bureau of the Census. 1971. U.S. Census of Population:
1970 Number of Inhabitants, Final Report PC(1) A12 Georgia.
U.S. Govt. Print. Off. Washington, D.C.
U.S. Environmental Protection Agency. 1975. National Eutro-
phication Survey Methods 1973-1976. Working Paper No. 175.
National Environmental Research Center, Las Vegas, Nevada,
and Pacific Northwest Environmental Research Laboratory,
Corvallis, Oregon.
Vollenweider, R. A., 1975. Input-Output Models With Final
Reference to the Phosphorus Loading Concept in Limnology.
Schweiz. A. Hydro1. 37: 53-84.
-------
VI. APPENDICES
APPENDIX A
CONVERSION FACTORS
-------
CONVERSION FACTORS
Hectares x 2.471 = acres
Kilometers x 0.6214 = miles
Meters x 3.281 = feet
-4
Cubic meters x 8.107 x 10 = acre/feet
Square kilometers x 0.3861 = square miles
Cubic meters/sec x 35.315 = cubic feet/sec
Centimeters x 0.3937 = inches
Kilograms x 2.205 = pounds
Kilograms/square kilometer x 5.711 = Ibs/square mile
-------
APPENDIX B
TRIBUTARY FLOW DATA
-------
TRIBUTARY FLOW INFORMATION FOR ALABAMA
07/22/76
LAKE cooe 0112
WEISS RESERVOIR
TOTAL DRAINAGE AREA OF LAKE(SO KM) 13649.3
SUR-ORAINAGE
TRIBUTARY AREAfSQ KM)
JAN
FEU
MAR
APR
MAY
NORMALIZED FLOWS(CMS)
JUN JJL AUG
SEP
OCT
NUV
DEC
SUMMARY
TOTAL DRAINAGE AREA OF LAKE =
SUM OF SUB-DRAINAGE AREAS =
13649.3
13650.3
TOTAL FLOW IN
TOTAL FLOW OUT
3934.99
3037.80
MEAN MONTHLY FLOWS AND DAILY FLOWSCCMSJ
TRIBUTARY MONTH YEAR MEAN FLOW DAY
0112A1
FLOW DAY
FLOW DAY
FLOW
0112A2
3
4
5
6
7
8
9
10
11
12
1
2
3
4
5
6
7
8
<}
10
11
12
1
2
73
73
73
73
73
73
73
73
73
73
74
74
73
73
73
73
73
73
73
73
73
73
74
74
447.406
467.228
467.228
402.099
153.194
109.586
116.099
122.329
138.186
222.287
600.317
498.376
547.478
542.636
519. 04R
438.600
201.644
140.225
112.928
152.968
187.316
357.953
715.963
679.208
3
5
2
1
5
8
13
3
9
5
2
3
8
5
2
1
4
8
13
4
9
5
2
165.937
336.970 8
764.555
116.949
75.040
103.356
115.533
109.869
164.804
758.891 19
379.446 16
138.186
695.745
227.101
2137.639
0.0
0.0
111.002
0.0
31.149
96.844
730.008 19
662.614 16
761.723
540.852
620.139
729.159
736.804
MEAN
0112M
0112A2
0112A3
0112U1
0112C1
011201
0112E1
0112F1
0112G1
0112H1
0112J1
0112K1
0112ZZ
10650.1
13649.3
13649.3
2?. 8
26.9
510.2
23.8
110.1
80.3
502.5
94.5
976.4
652.7
235.88
342.89
0.0
0.50
0.61
10.76
0.53
1.67
4.021
25.32
4.11
30.21
17.92
319.98
3B7.37
0.0
0.76
0.93
16.17
0.79
2.55
4.474
27.98
5.32
40.9?
24.92
404.93
466.38
0.0
0.8?
1.01
17.56
0.86
3.40
5.040
31.71
4.96
37.52
26.62
300.16
390.60
0.0
0.65
0.80
13.93
0.68
2.18
3.228
20.33
3.74
27.07
18.55
208.98
307.18
0.0
0.34
0.42
7.28
0.36
1.64
1.642
10.19
2.15
14.50
12.06
116.38
168.57
0.0
0.23
0.28
4.93
0.24
0.57
0.680
4.30
1.56
10.08
6.51
120.35
153.25
0.0
0.22
0.27
4.79
0.24
0.51
0.793
4.87
1.64
10.79
6.57
93.45
121.11
0.0
0.17
0.21
3.65
0.18
0.65
0.042
1.36
1.19
7.45
5.89
83.82
117.06
0.0
0.16
0.20
3.43
0.17
0.48
0.110
1.84
1.30
8.18
5.38
72.49
134.14
0.0
0.14
0.17
2.97
0.15
0.51
0.566
3.51
0.91
5.47
4.59
120.63
159.59
0.0
0.21
0.25
4.39
0.22
0.51
1.133
7.08
1.H4
12.18
6.94
154.61
289.65
0.0
0.32
0.39
6.80
0.33
0.65
2.492
15.49
2.52
17.39
9.46
185.21
252.53
0.0
0.37
0.46
8.00
0.39
1.27
2.006
12.76
2.59
18.34
12.04
-------
TRIBUTARY FLOW INFORMATION FOR ALABAMA
07/23/76
LAKE CODE 0112
WEISS RESERVOIR
MEAN MONTHLY FLOWS AND DAILY FLOWS
TRIBUTARY MONTH YEAR flEAN FLOW DAY
011243
0112B1
0112C1
U11201
3
4
5
6
7
8
9
10
11
12
1
2
3
4
5
6
7
B
9
10
11
12
1
2
3
4
5
6
7
8
9
10
11
12
1
?
3
4
5
6
7
a
9
10
11
12
1
2
73
73
73
73
73
73
73
73
73
73
74
74
73
73
73
73
73
73
73
73
73
73
74
74
73
73
73
73
73
73
73
73
73
73
74
74
73
73
73
73
73
73
73
73
73
73
74
74
FLOW DAY
FLOW DAY
FLOW
49.724
47.714
59.522
0.906
0.0
0.0
0.0
0.0
0.0
0.0
33.244
0.0
1.472
1.756
1.133
0.510
0.269
0.181
0.249
0.244
0.221
C.311
0.878
1.019
1.784
2.152
1.388
0.651
0.340
0.224
0.258
0.283
0.269
0.368
1.076
1.246
31.149
37.661
24.013
11.213
5.748
3.908
4.531
5.210
4.701
6.598
18.972
21.662
3
8
5
2
1
4
8
13
4
9
5
2
3
5
2
1
5
8
13
3
9
5
2
3
5
2
1
5
8
13
3
9
5
2
3
5
2
1
5
8
13
3
9
5
2
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0 19
0.0 16
0.566
0.878 8
0.453
0.311
0.210
0.190
0.238
0.244
0.232
0.906 19
0.510 16
0.680
1.246 8
0.510
0.255
0.142
0.122
0.176
0.181
0.170
1.388 19
0.595 16
11.893
19.850 8
9.628
5.890
3.823
3.398
4.474
4.531
4.332
20.671 19
10.760 16
0.0
0.0
2.832
0.481
1.841
8.495
0.538
4.248
76.455
9.911
89.198
-------
TRIBUTARY FLOW INFORMATION FOR ALABAMA
07/33/76
LAKE CODE 0113
WEISS RESERVOIR
MEAN MONTHLY FLOWS AND DAILY FLOWS
TRIBUTARY MONTH YEAR MEAN FLOW DAY
0112E1
0112F1
0112G1
0112H1
3
4
5
6
7
8
9
10
11
12
1
2
3
4
5
6
7
8
9
10
11
12
1
4
5
6
7
fl
9
10
11
12
1
3
4
5
6
7
8
9
10
11
12
1
?
73
73
73
73
73
73
73
73
73
73
74
74
73
73
73
73
73
73
73
73
73
73
74
74
73
73
73
73
73
73
73
73
73
73
74
74
73
73
73
73
73
73
73
73
73
73
74
74
FLOW OAY
FLOW DAY
FLOW
1.529
1.841
1.189
0.538
0.283
0.190
0.221
0.258
0.229
0.311
0.934
1.076
3.256
3.681
2.690
1.019
0.623
0.425
0.311
0.368
0.453
0.538
2.832
2.549
9.345
5.239
4.814
1.416
0.283
0.125
0.005
0.018
2.690
4.814
7.929
7.079
57.115
32.508
30.667
9.090
2.265
1.444
0.224
0.481
16.707
29.733
49.838
44.457
3
5
2
1
5
8
13
3
9
5
2
3
8
5
2
1
5
8
13
3
9
5
2
3
8
5
2
1
4
B
13
4
9
5
2
3
8
5
2
1
4
8
13
4
9
5
2
0.566
0.878 8
0.453
0.311
0.210
0.190
0.238
0.244
0.232
0.906 19
0.510 16
1.756
8.212
1.642
1.189
0.623
0.368
0.269
0.204
0.255
0.340
5.380 19
1.189 16
7.646
9.911
1.274
1.501
0.102
0.002
0.0
0.0
0.062
2.322
8.778 19
7.646 16
48.139
62.580
7.929
9.345
1.784
0.510
0.215
0.275
0.963
14.555
54.652 19
48.139 16
2.832
0.481
1.841
1.048
6.654
4.163
21.238
26.250
131.956
-------
TRIBUTARY FLOW INFORMATION FOR ALABAMA
07/22/76
LAKE CODE 0112
WEISS RESERVOIR
MEAN MONTHLY FLOWS AND DAILY FLOWS(CMS)
TRIBUTARY MONTH YEAR MEAN FLOW DAY
0112J1
0112K1
0112ZZ
3
4
5
6
7
8
9
10
11
12
1
2
3
4
5
6
7
8
9
10
11
12
1
2
3
4
5
6
7
8
9
10
11
12
1
?
73
73
73
73
73
73
73
73
73
73
74
74
73
73
73
73
73
73
73
73
73
73
74
74
73
73
73
73
73
73
73
73
73
73
74
74
FLOW DAY
FLOW DAY
FLOW
10.194
5.097
6.286
3.115
1.642
1.189
1.359
0.934
2.435
3.794
6.938
6.230
87.78?
40.493
50.970
22.653
11.044
7.646
8.778
5.465
12.176
17.387
30.214
40.918
43.183
28.062
28.175
12.459
6.853
4.899
4.757
3.993
8.297
12.771
30.327
26.873
3
8
5
2
1
4
8
13
4
9
5
2
3
8
5
2
1
4
8
13
3
9
5
2
3
a
5
2
1
4
8
13
3
9
5
2
5.947
10.619
2.265
3.341
1.642
1.104
0.878
0.708
0.821
2.407
6.938 19
6.938 16
47.855
92.313
15.744
24.494
11.015
7.051
5.352
4.134
4.814
16.990
56.917 19
56.917 16
23.984
59.975
12.374
13.819
6.909
4.361
3.341
2.605
3.115
7.815
39.191 19
25.032 16
3.794
13.026
28.883
116.099
14.781
63.288
-------
APPENDIX C
PHYSICAL AND CHEMICAL DATA
-------
STORE! RETRIEVAL DATE 76/07/22
011201
34 07 58.0 085 47 38.0 3
wtISS WESEKi/OIR
01019 ALAHAMA
033591
DATE
FROM
TO
73/03/19
73/06/07
73/08/25
73/10/30
DATE
FROM
TO
73/03/19
73/06/07
73/08/25
73/10/30
TIME DEPTH
OF
DAY
11 00
11 00
11 00
14 15
14 15
14 15
14 15
09 SO
09 50
09 SO
09 50
13 00
13 00
13 00
13 00
TIME
OK
OAV
11 00
11 00
11 00
14 15
1<> 15
14 15
14 15
09 SO
09 SO
U9 SO
09 SO
13 00
13 00
13 00
13 00
FEET
0000
0006
0019
0000
0005
0015
0030
0000
0005
0015
0027
0000
0005
0015
0026
DEPTH
FEET
OOCO
0006
0019
0000
0005
0015
0030
0000
0005
0015
0027
0000
0005
0015
0026
00010
HATER
TEMP
CENT
14. «
14.6
14.4
25.3
25.2
25.1
25.0
28.4
28.2
27.9
27.4
17.5
17.5
17.5
17.3
00665
PhOS-TOT
MG/L »
0.140
0.122
0 . 1 34
0.087
0.087
0.081
t.085
0.055
0.045
n.03d
0.037
0.076
0.077
0.076
0.084
00300
DO
MG/L
8.4
8.4
5.4
5.6
5.6
4.6
7.2
4.2
7.2
7.0
7.2
32217
CHLRPHYL
A
UG/L
3.6
6.9
9.7
4.1
00077 00094
TRtNSP CNDUCTVY
SECCHI FIELD
INCHES MICKOMHO
6 85
75
75
19 81
HI
80
80
34 120
121
127
117
37 114
114
113
113
11EPALES 2111202
0035 FEET DEPTH CLASS 00
00400 00410 00610 00625
PH
SU
7.40
7.50
7.50
7.00
6.30
6.90
6.9U
7.10
7.00
6.90
6.60
7.20
7.20
7.10
7.10
T ALK
CAC03
MO/L
27
26
27
35
36
36
36
46
45
45
45
50
49
50
50
NH3-IM
TOTAL
MG/L
0.140
0.110
0.110
0.150
0.130
0.120
0.020
0.040
0.040
0.080
0.160
0.140
0.140
0.130
0.140
TOT KJEL
N
MG/L
0.600
0.400
0.400
0.600
0.300
0.400
0.400
0.900
0.600
0.600
0.700
0.500
0.400
0.400
0.400
00630
N02&N03
N-TOTAL
MG/L
0.280
0.270
0.270
0.220
0.200
0.190
0.430
0.040
0.04U
0.050
0.060
0.140
0.120
0.120
0.120
00671
PHOS-DIS
ORTHO
MG/L P
0.035
0.035
0.034
0.034
0.032
0.032
0.044
0.010
0.012
0.009
0.012
0.043
0.042
0.041
0.041
-------
STOREF WETKIEVAL DATE 76/07/23
011203
34 10 27.0 085 45 16.0
••E1SS RESERVOIR
01019 ALABAMA
033591
11EPALES
2111202
0050 FEET DEPTH CLASS
DATE
FROM
TO
73/06/07
73/08/25
73/10/30
DATE
FWOM
TO
73/06/07
73/08/25
73/10/30
TIME DEPTH
OF
DAY FEET
14 SO 0000
14 SO 0005
14 50 0015
It 50 0030
14 SO 0046
10 40 0000
10 40 0005
10 40 0020
10 40 0045
12 35 0000
12 35 0005
12 .15 0015
12 35 0025
12 35 0042
TIMF DEPTH
OF
OAY FEET
14 50 0000
14 50 0005
14 50 0015
14 SO OU30
14 SO 004b
10 <>0 0000
10 40 0005
10 40 0020
10 40 0045
12 35 0000
12 35 0005
12 35 0015
12 35 0025
12 35 0042
00010
«/ATER
TEMP
CENT
25.2
25.3
25.2
25.6
24.9
28.2
28.2
28.2
27.3
17.8
17.8
17.7
17.7
17.7
00665
PHOS-TOT
MG/L P
•J.096
3.089
0.097
0.098
0.094
0.059
0.061
0.056
0.057
J.097
J.074
0.086
0.090
0.098
00300
DO
MG/L
5.8
5.6
5.8
5.2
6.8
8.0
4.0
6.9
7.2
7.0
R.O
32217
CHLRPHYL
A
UG/L
ft. 4
21. <•
6.0
00077 00094
THANSP CNDUCTVY
SECCHI FIELD
INCHES MICKOMHO
18 80
80
80
80
80
30 132
133
134
138
20 117
117
117
117
116
00400
PH
SU
6.90
6.90
6.90
6.90
6.90
7.30
7.40
7.00
7.10
7. 30
7.30
7.30
7.20
7.30
00410
T ALK
CAC03
MG/L
28
28
27
31
28
51
46
45
47
50
50
49
48
51
00610
NH3-N
TOTAL
MG/L
0.140
0.120
0.120
0.120
0.120
0.040
0.040
0.050
0.120
0.130
0.120
0.120
0.120
0.130
00
00625
TOT
N
KJEL
MG/L
0
0
0
0
0
0
0
0
0
0
0
0
0
0
.600
.300
.300
.300
.300
.600
.600
.600
.600
.500
.500
.400
.500
.400
00630
N02&N03
N-TOTAL
MG/L
0.200
0.200
0.190
0.190
0.190
0.040
0.030
0.040
0.030
0.110
0.110
0.110
0.100
0.100
00671
PHOS-DIS
O«THO
MG/L P
0.034
0.034
0.032
0.035
0.032
0.008
0.013
0.010
0.012
0.045
0.044
0.044
0.047
0.048
-------
STORE! RETRIEVAL DATE 76/07/33
011303
34 14 35.0 085 38 55.0 3
WEISS RESERVOIR
01019 ALABAMA
033591
11EPALES 3111203
0038 FEET DEPTH CLASS 00
DATE
FROM
TO
73/06/07
73/08/25
73/10/30
DATE
FROM
TO
73/06/07
73/08/35
73/10/30
TIME DEPTH
OF
DAY FEET
15 35 0000
15 35 0005
15 35 0015
15 35 0036
11 05 0000
11 05 0005
11 05 0015
11 05 0034
12 00 0000
12 00 0010
12 00 0025
12 00 0036
TIME DEPTH
OF
DAY FEET
15 35 0000
15 35 0005
15 35 0015
15 35 0026
11 05 0000
11 05 0005
11 05 0015
11 05 0034
12 00 0000
12 00 0010
12 00 0035
12 00 0036
00010
WATER
TEMP
CENT
25.2
24.5
24.1
24.0
27.5
27.3
27.2
26.6
16.1
16.1
16.1
16.0
00665
PHOS-TOT
MG/L P
0.094
0.084
0.092
0.093
0.099
0.096
0.084
0.091
0.137
0.139
0.152
0.141
00300
DO
MG/L
6.6
6.0
5.6
6.8
6.2
4.4
7.0
8.0
7.8
32317
CHLRPHYL
A
UG/L
10.8
22.0
9.8
00077 00094
TRANSP CNDUCTVY
SECCHI FIELD
INCHES MICROMHO
20 90
90
90
90
25 136
138
139
139
16 109
109
109
109
00400
PH
SU
6.90
6.90
6.90
6.90
7.80
7.50
7.40
7.60
7.50
7.40
7.50
00410
T ALK
CAC03
MG/L
33
34
33
34
47
48
48
48
48
48
47
49
00610
NH3-N
TOTAL
MG/L
0.100
0.090
0.120
0.110
0.040
0.040
0.070
0.150
0.110
0.090
0.100
0.110
00625
TOT KJEL
N
MG/L
0.400
0.300
0.400
0.300
0.500
0.600
0.700
0.700
0.500
0.300
0.300
0.400
00630
N02&N03
N-TOTAL
MG/L
0
0
0
0
0
0
0
0
0
0
0
0
.200
.190
.210
.200
.030
.040
.040
.070
.160
.150
.160
.150
00671
PHOS-DIS
ORTHO
MG/L P
0.039
0.027
0.030
0.024
0.020
0.017
0.020
0.022
0.077
0.075
0.078
0.077
-------
STORE! RETRIEVAL DATE 76/07/22
DATE
FROM
TO
73/06/08
73/08/25
73/10/30
TIME DEPTH
OF
DAY FEET
10 00 0000
10 00 0005
10 00 0015
10 00 0025
13 05 0000
13 05 0005
13 05 0015
13 05 0024
11 40 0000
11 40 0006
00010
WATER
TEMP
CENT
26.2
26.1
23.4
20.9
29.4
27.5
26.4
25.4
16.0
15.9
011204
34 11 48.0 085 39 57.0 3
WEISS RESERVOIR
01019 ALABAMA
033591
11EPALES 2111202
0029 FEET DEPTH CLASS 00
00300
DO
MG/L
8.8
3.8
2.4
3.4
2.2
0.1
7.8
00077
TRANSP
SECCHI
INCHES
21
26
18
00094
CNDUCTVY
FIELD
MICROMHO
85
80
60
80
156
151
137
151
204
203
00400
PH
SU
7.40
7.20
7.20
7.00
8.90
7.60
7.10
7.10
7.80
7.90
00410
T ALK
CAC03
MG/L
34
35
27
36
58
57
52
64
97
98
00610
NH3-N
TOTAL
MG/L
0.070
0.060
0.090
0.210
0.040
0.030
0.060
0.100
0.060
0.060
00625
TOT KJEL
N
MG/L
0.900
0.500
0.400
0.400
1.000
0.700
0.500
0.600
0.500
0.700
00630
N02&N03
N-TOTAL
MG/L
0.070
0.050
0.130
0.130
0.040
0.030
0.040
0.080
0.050
0.040
00671
PHOS-D1S
ORTHO
MG/L P
0.006
0.005
0.005
0.004
0.009
0.007
0.005
0.009
0.044
0.043
00665 32217
DATE TIME DEPTH PHOS-TOT CHLRPHYL
FROM OF ' A
TO DAY FEET MG/L P UG/L
73/06/Ott 10 00 0000 0.050 6.5
10 00 0005 0.045
10 00 0015 0.039
10 00 0025 0.032
73/08/25 13 05 0000 0.056 18.8
13 05 0005 C.052
13 05 0015 0.058
13 05 0024 0.066
73/10/30 11 40 0000 0.134 25.2
11 40 9008 O.lbO
-------
STORET RETRIEVAL DATE 76/07/22
OH205
34 09 30.0 085 36 12.0 3
WEISS RESERVOIR
01019 ALABAMA
033591
DATE
FROM
TO
73/06/08
73/08/25
DATE
PROM
TO
73/06/08
73/08/25
TIME DEPTH
OF
DAY FEET
10 40 0000
10 40 0005
10 40 0010
10 40 0015
10 40 0030
13 40 0000
13 40 0005
13 40 0015
13 40 0025
TIME DEPTH
OF
DAY FEET
10 40 0000
10 40 0005
10 40 0010
10 40 0015
10 40 0030
13 40 0000
13 40 0005
13 40 0015
13 40 0025
00010
WATER
TEMP
CENT
24.6
23.1
22.2
22.2
21.9
28.7
27.2
26.7
26.6
00665
PHOS-TOT
MG/L P
0.075
0.092
0.117
0.120
0.162
0.100
0.115
0.116
0.096
00300
DO '
MG/L
6.6
6.4
6.0
5.8
7.2
4.6
4.7
32217
CHLRPHYL
A
UG/L
9.4
12.6
00077 00094
TRANSP CNDUCTVY
SECCHI FIELD
INCHES MICROMHO
20 80
80
80
80
80
32 136
135
133
133
11EPALES 2111202
0034 FEET DEPTH CLASS 00
00
-------
STORE! RETRIEVAL DATE 76/07/32
011206
34 13 57.0 085 30
WEISS RESERVOIR
01019 ALABAMA
15.0 3
033591
DATE
FROM
TO
73/06/08
73/08/25
73/10/30
DATE
FROM
TO
73/06/08
73/08/25
73/10/30
TIME DEPTH
OF
DAY FEET
11 10 0000
11 10 0005
11 10 0015
11 10 0030
13 55 0000
13 55 0005
13 55 0015
13 55 0028
12 20 0000
TIME DEPTH
OF
DAY FEET
11 10 0000
11 10 0005
11 10 0015
11 10 0030
13 55 0000
13 55 0005
13 55 0015
13 55 0028
12 20 0000
00010
WATER
TEMP
CENT
22.4
22.0
21.6
21.5
27.3
27.2
27.0
27.0
16.0
00665
PHOS-TOT
MG/L P
0.087
C.I 36
0.146
0.148
0.167
0.154
0.145
0.120
0.117
00300
DO
MG/L
6.6
6.4
6.4
5.0
5.2
5.0
8.2
32217
CHLRPHYL
A
UG/L
6.7
3.7
17.1
00077 00094
TRANSP CNDUCTVY
SECCHI FIELD
INCHES MICROMHO
8 85
82
80
80
26 138
136
136
138
13 103
11EPALES 2111202
0034 FEET DEPTH CLASS 00
00400 00410 00610 00625
PH
su
6
7
7
7
7
7
7
7
7
.90
.00
.00
.00
.30
.20
.10
.20
.50
T ALK
CAC03
MG/L
25
27
27
26
45
46
45
45
45
NH3-N
TOTAL
MG/L
0.100
0.100
0.110
0.120
0.080
0.080
0.080
0.080
0.080
TOT KJEL
N
MG/L
0.600
0.500
0.600
0.500
0.700
0.600
0.600
0.500
0.500
00630
N02&N03
N-TOTAL
MG/L
0.240
0.250
0.270
0.300
0.300
0.300
0.300
0.300
0.090
00671
PHOS-DIS
ORTHO
MG/L P
0.023
0.038
0.045
0.046
0.115
0.100
0.092
0.081
0.045
-------
APPENDIX D
TRIBUTARY AND WASTEWATER
TREATMENT PLANT DATA
-------
STORET RETRIEVAL DATE 76/07/22
OH2A1 13X2A1
34 15 00.0 035 21 30.0 4
COOSA RIVER
01 7.5 LIVINGSTON 6
I/WEISS KESVR 033591
BRDG ON GA RT 100 W OF ROME
11EPALES 2111204
0000 FEET DEPTH CLASS 00
DATE
FROM
TO
73/03/03
73/04/05
73/04/06
73/C6/02
73/07/01
73/08/05
73/09/08
73/10/13
73/11/03
73/12/09
74/01/05
7W01/19
74/02/02
74/02/16
00630 00625
TIME DEPTH N026.N03 TOT KJEL
OF N-TOTAL N
DAY FEET
14
15
10
15
08
10
10
16
16
10
11
10
10
10
30
30
30
A5
55
15
15
50
?0
so
45
45
50
45
MG/L
0
0
0
0
0
0
0
0
0
0
0
0
0
0
.270
.250
.270
.132
.220
.210
.220
.200
.150
.216
.240
.312
.300
.240
MG/L
1.
?.
1.
2.
1.
0.
0.
0.
0.
0.
0.
0.
0.
0.
100
700
150
200
700
350
870
420
550
300
900
200
200
500
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.
096
090
138
560
105
067
110
062
052
016
076
032
025
020
MG/L
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
p
165
054
062
042
113
125
140
138
048
040
040
045
045
MG/L P
0.250
0.115
0.200
0.125
0.175
0.185
0.250
0.200
0.350
0.160
0.115
0.120
0.115
0.195
-------
bTORET RETRIEVAL DATE 76/07/22
0112A2 LS0112A2
37 08 00.0 085 4? 30.0 4
COOSA RIVER
01 7.5 LEESBURG
0/WEISS RESVR 051691
bELO DAM ACROSS LAKE AND Srt OP LEESBllRG
11EPALES 211120^
0000 FEET DEPTH CLASS 00
DATE
FROM
TO
73/03/03
73/04/08
73/05/05
73/06/02
73/07/01
73/08/04
73/09/08
73/10/13
73/1 1/0<*
73/12/09
74/61/05
74/01/19
74/02/02
74/02/16
00630 00625
TIME DEPTH N02&N03 TOT KJEL
OF N-TOTAL N
DAY FEET
09
08
14
14
08
18
14
16
09
09
11
10
10
10
20
50
45
30
05
10
40
00
15
30
00
00
00
00
MG/L
0
0
0
0
0
->
0
0
a
0
0
0
0
0
.220
.231
.150
.150
.022
.010K
.011
.130
.120
.232
.216
.300
.276
.290
MG/L
0.
1.
3.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
675
570
600
560
460
600
600
560
400
300
400
700
500
300
00610 00671 00665
NH3-N PHOS-DIS PHOS-TOT
TOTAL. ORTHO
MG/L
U.
0.
G.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
046
075
115
096
024
014
030
138
074
084
056
076
040
035
MG/L
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
a.
0.
p
058
040
022
048
012
006
012
046
055
064
040
036
040
030
MG/L P
0.095
0.090
0.080
0.137
0.045
0.065
0.055
0.085
0.105
0.105
0.140
0.090
0.090
0.075
K VALUE KNOWN TO HE
LESS THAN INDICATED
-------
STORLF RETRIEVAL DATE 76/07/22
011?A3 LS0112A3
34 10 30.0 065 45 30.0 4
COOSA RIVEK
01 7.5 LtESbUhiG
0/rtEIS RESVH 033591
dELO 'WEISS DAM BEFOK CON WITH MAINSTREAM
11EPALES 2111204
0000 FEET DEPTH CLASS 00
DATE
FROM
TO
73/03/03
73/04/08
73/05/05
73/06/02
73/07/01
73/OB/0<*
73/09/06
73/10/13
73/11/04
73/12/09
74/01/05
74/01/19
74/02/02
74/02/16
00630 00625
TIME DEPTrt N026.N03 TOT KJEL
OF N- TOTAL N
DAY FEET
u9
09
15
15
08
17
14
16
09
09
10
09
09
09
40
05
00
00
?4
45
15
15
00
00
45
35
00
40
MG/L
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
200
220
154
140
071
092
018
180
120
224
240
300
300
276
MG/L
0.
1.
1.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
720
260
050
690
520
520
480
620
550
400
800
200
400
200
00610 00671 00665
NH3-N PHOS-OIS PHOS-TOT
TOTAL ORTHO
MG/L
0.
0.
0.
0.
0.
0.
c.
0.
0.
0.
0.
0.
0.
0.
042
058
048
092
115
154
113
138
110
072
100
040
070
030
MG/L P
0
0
0
0
0
0
0
0
0
0
0
0
0
0
.042
.039
.025
.046
.021
.024
.012
.046
.050
.064
.040
.036
.045
.030
MG/L P
0.085
0.090
0.085
0.135
0.055
0.065
0.060
0.080
0.090
0.110
U.130
0.085
0.090
0.075
-------
STORET RETRIEVAL DATE 76/07/22
0112dl 13A2B1
34 15 00.0 085 24 30.0 4
MF rlOPE CKtEK
01 7.5 MELSON GA-AL
T/*EISS RESVR 033591
bROG ON OLD RVR RD 2.8 MI E OF ALABAMA
11EPALES 2111204
0000 FEET DEPTH CLASS 00
DATE
FROM
TO
73/03/03
73/04/05
73/04/08
73/06/02
73/07/01
73/08/05
73/09/08
73/10/13
73/11/03
73/12/09
74/01/05
74/01/ls
74/02/02
74/02/16
00630 00625
TIME DEPTH N02&N03 TOT KJEL
OF N-TOTAL N
DAY FEET
14
16
10
16
08
10
10
17
16
11
12
11
11
11
10
00
45
20
40
40
35
10
4?
10
00
10
?0
00
MG/L
0
0
0
0
0
0
0
c
0
j
0
0
0
0
.130
.190
.126
.160
.210
.198
.230
.198
.189
.264
.240
.276
.192
.108
MG/L
0.
3.
0.
2.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
2flO
250
880
000
390
100K
290
220
200
500
100
300
1!)OK
500
00610 00671 00665
NH3-N PHOS-OIS PHOS-TOT
TOTAL ORTHO
MG/L
0
0
0
0
0
0
0
0
0
0
u
0
c
a
.022
.063
.060
.600
.040
.027
.034
.024
.048
.036
.024
.120
.010
.030
MG/L
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
o.
0.
p
017
009
008
013
010
017
005K
009
008
012
005
010
015
MG/L P
0.030
0.020
0.025
0.025
0.030
0.020
0.025
0.025
0.025
0.015
0.020
0.025
0.025
0.075
K VALUE KNOWN ro HE
LESS THAN INDICATED
-------
STORET RETRIEVAL DATE 76/07/22
0112C1 13X2C1
34 15 00.0 085 25 30.0 4
KING CkEEK
01 7.5 CHATTOGAVILL
T/WE1SS RtSVR 033591
BRDG ON OLD RIVER K[) 2 MI E OF ALABAMA
11EPALES 2111204
0000 FEET DEPTH CLASS 00
DATE
FkOM
TO
73/03/03
73/04/05
73/04/08
73/06/0?
73/07/01
73/08/05
73/09/08
73/10/13
73/11/03
73/12/09
74/01/05
74/01/19
74/02/02
74/02/16
00630 00625
TIME DEPTH N02&.N03 TOT KJEL
OF N-TOTAL N
DAY FEET
14
16
11
16
08
11
10
17
16
11
12
11
11
11
00
10
00
30
35
00
45
15
55
50
15
?0
?5
20
MG/L
0.073
0.147
0.066
0.115
0.150
0.138
0.072
0.075
0.052
0.156
0.120
0.176
U.132
0.052
MG/L
0.210
1.470
1.200
2.100
0.110
0.140
0.310
0.200
0.200
0.300
0.600
0.100
0.100K
0.600
00610 00671 00665
NH3-N PHOS-DIS PHOS-TOT
TOTAL ORTHO
MG/L
0.018
0.048
0.042
0.066
0.018
0.029
0.024
0.009
0.033
0.024
0.048
0.015
0.005
0.020
MG/L P
0.008
0.005K
0.005K
0.008
0.006
0.005K
0.005K
0.005K
0.005K
0.008
0.005K
0.005
0.010
MG/L P
0.015
0.010
0.015
0.015
0.010
0.015
O.OlU
0.010
0.010
0.010
0.010
0.010
0.010
0.050
K VALUE KNO*N TO BE
LESS THAN INDICATED
-------
STORE! RETRIEVAL DATE 76/07/82
0112D1 13X201
34 10 00.0 085 20 30.0 4
«IG CEDAR CREEK
01 7.5 LIVINGSTON
T/rtEISS RESVR 033591
BRDG ON KT 100 AT FOSTE MILLS
11EPALES 2111204
0000 FEET DEPTH CLASS 00
DATE
FROM
TO
73/03/03
73/04/05
73/04/Od
73/06/02
73/07/01
73/08/05
73/09/08
73/10/13
73/11/03
73/12/09
74/01/05
74/01/19
74/02/02
74/02/16
00630 00625
TIME DEPTH N02&N03 TOT KJEL
OF N-TOTAL N
DAY FEET
14
14
10
15
09
09
10
16
16
10
11
10
10
10
40
S5
00
30
10
45
00
30
05
30
30
20
30
30
MG/L
0
0
0
0
0
0
0
0
0
0
0
0
0
0
.240
.320
.290
.390
.330
.150
.410
.510
.250
.216
.400
.504
.528
.300
MG/L
1.
2.
2.
1.
0.
0.
0.
0.
050
900
940
380
220
460
680
200
0.200
0.
0.
0.
0.
1.
100K
350
200
300
000
00610 00671 00665
NH3-N PHOS-DIS PHOS-TOT
TOTAL ORTHO
MG/L
C.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
036
210
150
231
017
022
067
015
048
005K
032
064
060
135
MG/L
0.
0.
0.
0.
0.
0.
0.
0.
o.
0.
0.
0.
0.
p
037
071
036
042
063
042
100
115
080
036
048
045
045
MG/L P
0.070
0.075
0.110
0.070
0.085
0.070
0.150
0.130
G.I 30
0.095
0.075
0.080
0.070
0.185
K VALUE KNOWN TO 8E
LESS THAN INDICATED
-------
STORE! RETRIEVAL DATE 76/07/23
0112E1 13X2E1
34 10 00.0 085 26 00.0 4
MdQ CHEEK
01 7.5 MELSON GA-AL
T/wtlSS RESVR 033591
tsRDG GEOKGE WO .9 MI Sw OF BLACK 6LUF RO
11EPALES 2111204
0000 FEET UtPTH CLASS 00
DATE
FROM
TO
73/03/03
73/04/05
73/04/08
73/06/02
73/07/01
73/08/05
73/09/08
73/10/13
73/11/03
73/12/09
7^/01/05
74/01/19
74/02/02
74/02/16
00630 00625
TIME DEPTH N02kN03 TOT KJEL
OF N-TOTAL N
OAY FEET
15
14
09
15
09
09
09
16
15
10
11
10
10
10
on
30
30
00
25
15
30
15
45
00
15
00
00
00
MG/L
C
0
0
0
0
0
0
0
0
0
0
0
0
0
.056
.023
.046
.036
.031
.040
.066
.032
.011
.012
.012
.020
.040
.036
MG/L
1.
2.
2.
2.
0.
0.
1.
0.
0.
0.
1.
0.
0.
0.
680
310
600
700
675
630
050
610
500
300
100
300
300
700
00610 00671 00665
NH3-N PnOS-DIS PHOS-TOT
TOTAL ORTHO
MG/L
0.
0.
0.
0.
0.
0.
G.
0.
0.
0.
0.
J.
0.
0.
063
093
360
190
069
039
070
025
018
012
020
020
020
045
MG/L
0.
0.
0.
0.
0.
0*
0.
0.
0.
0.
0.
0.
0.
p
019
006
Oil
008
010
005K
007
005K
005K
012
OOH
010
010
MG/L P
0.045
0.015
0.040
0.020
0.030
0.025
0.060
0.025
0.020
0.015
0.025
U.030
0.025
0.047
K VALUE KNOWN TO HE
LESS THAN INDICATED
-------
bTORET RETRIEVAL DATE 76/07/22
0112F1 LS0112F1
34 07 30.0 085 32 00.0 *
SPRING CREEK
01 7.5 CEDAR BLUFF
T/wEISS RESVR 033591
HRDG ON SEC RO 1.5 W OF WHARTON
11EPALES 2111204
0000 FEET DEPTH CLASS 00
DATE
FROM
TO
73/03/03
73/04/05
73/04/Ort
73/06/02
73/07/01
73/08/05
73/09/08
73/10/13
73/11/03
73/12/09
74/01/05
74/01/19
74/02/02
74/02/16
00630 00625
TIMF DEPTH N02&N03 TOT KJEL
OF N-TOTAL N
DAY FEET
15
14
09
14
09
08
09
15
15
09
10
09
09
09
?5
10
05
30
50
50
15
50
25
30
50
30
30
30
MG/L
0.
0.
0.
0.
0.
0.
0.
0.
0.
c.
0.
0.
0.
0.
198
350
105
280
240
138
090
054
014
104
368
490
470
140
MG/L
0.
1.
1.
2.
0.
0.
0.
0.
4.
0.
0.
0.
0.
0.
770
680
000
400
210
270
690
290
300
200
200
200
100K
800
00610 00671 00665
NH3-N PHOS-OIS PHOS-TOT
TOTAL ORTHO
MG/L
0.
0.
0.
0.
0.
0.
0.
0.
042
044
038
220
021
022
082
015
MG/L
0.
0.
0.
0.
0.
0.
0.
0.
p
022
006
023
009
012
005K
005K
007
0.018
0.
C.
0.
0.
0.
040
024
012
010
050
0.
0.
0.
0.
0.
008
028
008
010
070
MG/L P
o.oao
0.015
0.070
0.025
0.045
0.025
0.025
0.020
0.015
0.020
0.040
0.030
0.025
0.210
K VALUE KNOWN TO HE
LESS THAN INDICATED
-------
STORET RETRIEVAL DATE 76/07/22
LS0112G1
34 19 30.0 085 44 30.0 4
YELLOW CREEK
01 7.5 CENTRE AL
T/WE1SS RESVR 033591
BROG ON RD 4 MI NNfc OF LEESBURG
11EPALES 2111204
0000 FEET DEPTH CLASS 00
DATE
FROM
TO
73/03/03
73/04/08
73/05/05
73/06/02
73/07/01
73/08/04
73/09/OB
73/10/13
73/11/04
73/12/09
74/01/05
74/01/19
74/02/02
74/02/16
00630 00625
TIME DEPTH N02&N03 TOT KJEL
OF N- TOTAL N
DAY FEET
10
09
16
15
10
18
13
16
09
10
11
10
10
10
30
30
00
30
00
?0
45
45
55
00
15
30
30
20
MG/L
0
0
0
0
0
0
0
0
0
0
0
0
c
0
.550
.410
.460
.320
.320
.230
.010K
.018
.019
.880
.980
.930
.730
.504
MG/L
1.
2.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
050
400
580
320
230
210
560
750
800
100
300
100K
600
300
00610 00671 00665
NH3-N PHOS-OIS PHOS-TOT
TOTAL ORTHO
MG/L
0.
0.
0.
0.
0.
c.
0.
0.
0.
0.
0.
0.
0.
0.
061
096
032
050
030
017
027
037
039
040
048
040
300
020
MG/L
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
p
014
Oil
005K
009
008
005K
005K
015
012
008
008
005K
015
015
MG/L P
0.050
O.U40
0.015
0.020
0.020
0.015
0.025
0.080
0.050
0.010
0.015
0.040
0.060
0.055
K y/ALUE KNOWN TO BE
LESS THAN INDICATED
-------
STORET RETRIEVAL DATE 76/07/2?
0112-11 LS0112H1
3* 17 00.0 085 40 30.0 4
LITTLE RIVER
01 7.5 LITTLE RIVER
T/WE1SE RESVR 033591
BROG ON CO RT 15 IN VLG OF LITTLE RIVER
HEPALES 2111204
0000 FEET DEPTH CLASS 00
DATE
FROM
TO
73/03/03
73/04/08
73/05/05
73/06/02
73/07/01
73/06/04
73/09/08
73/10/13
73/11/04
73/12/09
74/01/05
74/01/19
7W02/02
74/02/lb
00630 00625
TIME DEPTH N02NN03 TOT KJEL
OF N-TOTAL N
DAY FEET
10
09
16
16
10
19
12
17
10
10
12
11
09
10
40
50
30
00
30
00
55
45
30
40
00
00
10
40
MG/L
0
0
0
0
0
0
0
0
0
0
0
0
0
0
.210
.160
.110
.060
.050
.010K
.010K
.G10K
.015
.232
.300
.312
.288
.216
MG/L
0.
1.
4.
1.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
520
380
000
470
160
150
400
240
550
100
400
100K
400
400
OP610 00671 00665
NH3-N PHOS-DIS PHOS-TOT
TOTAL ORTHO
MG/L
0.
0.
0.
0.
0.
c.
0.
0.
0.
0.
0.
0.
0.
0.
037
072
110
190
Oil
019
021
026
048
028
040
016
040
025
MG/L
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
p
006
005K
005K
006
005K
005K
005K
005K
005K
005K
008
005*
005
005
MG/L P
0.020
0.015
0.010
0.020
0.005K
0.010
0.015
0.010
0.035
0.005K
0.008
0.010
0.030
0.080
K VALUE *NO.'iN TO BE
LESS THAN INDICATED
-------
STORET RETRIEVAL DATE 76/07/22
0112J1 LS0112J1
34 16 .10.0 085 37 JO.O 4
SPRING CREEK (N)
01 7.5 GALEYSVILLE
T/WEISS RESVR 033591
ttROG ON CO RT 75 NEAR HURLEY
11EPALES 2111204
0000 FEET DEPTH CLASS 00
DATE
FROM
TO
73/03/03
73/04/08
73/05/05
73/06/02
73/07/01
73/08/0^
73/09/08
73/10/13
73/11/04
73/12/09
74/01/05
74/01/19
74/02/0?
74/02/16
00630 00625
TIME DEPTH N02&N03 TOT KJEL
OF N-TOTAL N
DAY FEET
11
10
16
16
09
19
12
18
10
11
12
11
11
10
05
05
45
15
00
20
40
00
55
20
35
30
30
55
MG/L
C
0
0
U
0
0
C
0
0
0
0
0
0
0
.470
.273
.399
.336
.410
.390
.357
.300
.350
.480
.430
.460
.216
.156
MG/L
0.
3.
1.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
705
900
890
180
100K
110
270
200
200
200
200
100
250
500
00610 00671 00665
NH3-N PHOS-OIS PnOS-TOT
TOTAL ORTHO
MG/L
0.
0.
0.
0.
0.
0.
0.
0.
C.
0.
0.
0.
0.
0.
092
120
052
022
018
006
014
012
Oil
012
012
008
012
015
MG/L
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
p
024
008
005K
007
005K
005K
005K
005K
005K
005K
008
005K
015
020
MG/L P
0.075
0.035
0.015
0.022
0.015
0.020
0.015
0.015
0.025
0.010
0.025
0.020
0.063
0.135
K VALUE KNOWN TO d£
LESS THAN INDICATED
-------
STORET RETRIEVAL DATE 76/07/32
OU2K1 LS0112K1
34 16 00.0 085 33 30.0 4
CHATTOOGA *IVtK
01 7.5 GALEYSVILLE
T/WEISS RESVR 033591
BRDG ON ST RT 35 IN GAYLESVILLE
11EPALES 2111204
0000 FEET DEPTH CLASS 00
DATE
FROM
TO
73/03/03
73/04/08
73/05/05
73/06/02
73/07/01
73/08/04
73/09/08
73/10/U
73/11/03
73/12/09
74/01/05
74/01/19
74/02/02
74/02/16
00630 00625
TIME DEPTH N02&N03 TOT KJEL
OF N-TOTAL N
DAY FEET
11
10
16
16
09
19
11
18
12
13
12
12
11
20
20
55
30
35
30
15
20
00
30
00
00
1C
MG/L
0
C
0
0
0
0
0
0
0
0
0
0
0
0
.390
.273
.420
.340
.480
.640
.590
.490
.390
.450
.370
.<*60
.384
.240
MG/L
1.
4.
1.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
800
000
050
990
340
620
720
790
750
300
200
300
300
600
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.
132
132
080
072
028
080
100
054
075
036
024
032
020
050
MG/L
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
P
154
094
105
080
120
294
565
530
032
046
072
060
055
MG/L P
0.300
0.210
0.155
0.133
0.175
0.355
0.620
0.67!)
0.880
0.165
0.095
0.120
0.14Q
0.200
-------
STORET RETRIEVAL DATE 76/07/33
0112AA TF0112AA P060000
34 15 00.0 085 15 00.0 4
KOME (GEORGIA)
01 1:250000 KOME
T/WEISS RESERVOIR 033591
COOSA RIVER
11EPALES 2141304
0000 FEET DEPTH CLASS 00
DATE
FROM
TO
73/04/17
CP(T>-
73/04/17
73/05/15
CP(T)-
73/05/lb
73/06/16
73/07/17
CP-
73/07/17
73/08/20
CP(T)-
73/08/20
73/09/23
CP(T)-
73/09/23
73/10/18
CPITI-
73/10/18
73/11/22
CP-
73/11/22
74/06/1H
CP(T>-
74/06/18
74/li)/ 16
CP-
74/10/16
74/12/17
CP(T>-
74/12/17
75/01/09
CPUI-
75/01/09
75/04/22
CP(T)-
75/04/2?
00630 00625
TIME DEPTH N02&N03 TOT KJEL
OF M-TOTAL N
DAY FEET MG/L MG/L
00
24
00
03
00
02
00
24
00
03
00
24
00
24
00
04
00
02
00
04
00
02
UO
04
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
0
3
0
0
0
0
0
0
0
0
0
0
0
.025
.700
.280
.010K
.013
.100
.650
.160
.230
.080
.160
.080
.100
14.000
10.500
12.000
13.800
18.000
15.400
12.500
16.000
13.000
13.000
13.500
7.200
6.600
00610
NH3-N
TOTAL
MG/L
3.000
3.100
3.600
2.817
2.960
3.300
3.000
6.500
2.900
1.500
2.100
0.790
0.650
00671
PHOS-DIS
ORTHO
MG/L P
11.800
4.700
11.200
3.990
9.350
6.100
4.700
5.100
5.100
11.000
6.400
5.900
10.520
00665
PHOS-TOT
MG/L P
15.700
12.000
14.500
7.900
14.000
7.500
7.400
5.900
6.100
9.700
7.100
13.000
50051 50053
FLOW CONDUIT
RATE FLOw-MGD
INST MOD MONTHLY
11
8
7
8
6
4
6
4
3
8
4
5
7
.700
.060
.500
.400
.990
.110
.860
.990
.300
.660
.640
.050
.840
9.080
7.820
7.700
7.230
7.230
5.920
6.630
6.770
3.190
6.100
5.500
4.500
7.050
K VALUE KNOWN TO BE
LESS THAN INDICATED
-------
STOWEF RETRIEVAL DATE 76/07/33
0112DA TF0112DA P007000
34 01 00.0 085 15 45.0 4
CEOA«TO»N (GEORGIA)
01 1:250000 ROME
T/WEISS RESERVOIR 033591
dlG CEDAR RIVER
11EPALES 2141304
0000 FEET DEPTH CLASS 00
DATE
FROM
ro
73/05/01
CPIT1-
73/05/01
73/07/09
CPIT1-
73/07/09
73/08/03
CPIT1-
73/08/03
73/09/04
ChMT)-
73/09/04
73/10/04
CPITI-
73/10/04
73/11/09
CfMT)-
73/11/09
73/13/06
CPIT1-
73/13/06
64/01/03
CPITJ-
74/01/02
74/03/Ob
CP(T)-
7«./02/05
74/03/05
CP(T>-
74/03/05
74/04/05
CP-
74/0«/05
00630 00b?5 00610 00671 00665 50051 50053
TIME DEPTH N02&N03 TOT KJEL NH3-N PHOS-DIS PHOS-TOT FLO* CONDUIT
OF N-TOTAL N TOTAL ORTHO RATE FLOrt-MGD
DAY FEET MG/L MG/L MG/L MG/L P MG/L P INST MGD MONTHLY
11
16
11
16
11
16
11
16
11
16
11
16
11
16
11
16
11
16
11
16
11
16
00
00
00
00
00
00
00
no
00
00
00
00
00
00
00
00
00
00
00
no
00
00
3.000
3.600
3.540
0.290
0.780
0.880
1.480
li.360
0.920
3.200
4.100
1.200
7.700
8.000
10.500
5.700
3.300
8.300
5.800
l.OOOK
0.074
0.410
0.1 BO
1.100
2.940
0.430
0.330
0.240
0.170
0.150
2.500 3.175
5.300 7.050
8.840
7.000 8.200
7.700 8.600
6.200 8.050
2.800 3.300
4.200 5.500
11.000 12.000
2.700 3.400
1
1
0
0
0
0
0
0
1
1
1
.120
.500
.854
.807
.838
.855
.871
.930
.060
.210
.210
1
1
0
0
0
0
0
0
1
1
0
.140
.300
.745
.831
.850
.773
.830
.875
.090
.120
.978
K VALUE KNOWN TO 8E
LESS THAN INDICATED
-------
STORE.! RETRIEVAL DATE 76/07/22
00630
DATE TIME DEPTH N02*,N03
FROM OF N-TOTAL
TO DAY FEET MG/L
00625
TOT KJEL
N
MG/L
00610
NH3-N
TOTAL
MG/L
00671
PHOS-DIS
ORTHO
MG/L P
01l2Dtt AS01120B P
34 07 10.0 085 20 10.0 4
CAVE SPRINGS
01 FLOYD CO GA HWY
T/LAKE WEISS 033591
CEDAK CREEK
11EPALES 2141204
0000 FEET DEPTH CLASS 00
00665 50051 b0053
PHOS-TOT FLOw CONDUIT
RATE FLOW-MGD
MG/L P INST MGO MONTHLY
P002200
73/10/01
CP-
73/10/0?
16 00
03 00
0.110
2.100
0.092
2.500
3.000
4.750
4.OHO
-------
STORE! RETRIEVAL DATE 76/07/22
00630
DATE TIME DEPTH N02&N03
FROM OF N-TOTAL
TO QAr FEET MG/L
73/04/03 07 30
73/05/07 07 00
73/06/05
73/07/05 09 00
73/08/10 18 00
73/09/10 06 00
73/10/Ofl 00 00
73/11/05 15 00
73/12/05 15 00
O.blO
29.600
31.000
18.800
38.400
42.000
35.000
29.000
28.000
0112KA PU0112KA POOOObO*
34 12 50.0 085 36 bO.O 4
BURGESS MANUFACTURING
01 7.5 CEDAR BLUFF
T/rtEISS RESERVOIR 033591
CHATTOOGA RIVtR
11EPALES
2141204
0000 FEET DEPTH CLASS 00
00625
TOT KJEL
N
MG/L
9.900
9.950
17.600
16.800
12.400
10.500
7.400
7.600
13.000
00610
NH3-N
TOTAL
MG/L
3.000
9.950
13.000
6.000
10.130
7.200
6.800
5.900
00671
PHOS-DIS
ORTHO
MG/L P
2.950
2.000
2.300
1.680
2.100
0.975
1.260
2.000
1.760
00665
PHOS-TOT
MG/L P
4.300
3.100
3.800
3.700
3.400
5.000
2.800
4.900
3.900
50051
FLOW
RATE
INST MGD
0.010
0.010
0.010
o.uio
0.010
0.010
0.010
0.010
50053
CONDUIT
FLOW-MGD
MONTHLY
0.010
0.010
0.010
0.010
0.010
0.010
0.010
0.010
-------
STORET RETRIEVAL DATE 76/07/22
0112KH AS0112Ktt P0040001
34 58 00.0 085 05 30.0 4
SUMMERVILLE (GEORGIA)
01 1:250000 HOME
T/WEISS RESERVOIR 040892
MT HOPE CREEK
11EPALES 2141204
0000 FEET DEPTH CLASS 00
DATE
FROM
TO
73/04/16
73/05/23
73/06/20
73/07/19
73/08/16
73/09/17
73/10/17
73/11/16
73/12/17
74/01/17
74/04/OH
00630
TIME DEPTH N02NN03
OF N-TOTAL
DAY FEET
16
15
09
08
11
09
11
09
12
00
00
00
30
00
00
10
00
30
MG/L
2.200
4.400
2.500
4.700
1.050
6.400
8.000
3.800
0.720
0.560
0.920
00625
TOT KJEL
N
MG/L
3.700
2.525
1.900
2.200
2.300
1.700
2.200
11.000
1.200
1.400
00610 00671
NH3-N PH05-DIS
TOTAL ORTHO
MG/L
0.360
0.130
0.840
0.096
0.130
0.200
0.150
0.097
0.220
0.040K
0.068
MG/L P
8.900
8.400
14.600
10.200
6.000
15.200
4.900
20.000
8.600
5.900
6.000
00665
PHOS-TOT
50051 50053
FLOh CONDUIT
RATE FLOrf-MGD
MG/L P INST
9
9
16
11
15
15
19
21
11
7
7
.300
.400
.000
.500
.700
.500
.500
.000
.000
.330
.000
1
1
1
1
1
1
1
1
1
1
MOD MONIHLY
.100
.100
.ICO
.100
.ICO
.100
.100
.100
.ICO
.100
1.100
1.100
1.100
1.100
1.100
1.100
1.100
1.100
1.100
1.100
K VALUE KNOWN TO BE
LESS THiN INDICATED
-------
STORE! RETRIEVAL DATE
0112KC AS0112KC P050500
34 33 00.0 085 06 30.0 4
TRION (GEORGIA)
01 1:250000 ROME
T/WEISS RESERVOIR 033591
CHATOOGA KIVER
11EPALES 2141204
0000 FEET DEPTH CLASS 00
DATE
FROM
TO
73/04/30
CP-
73/04/30
73/05/2**
CPIT1-
73/05/29
73/Ob/29
CP(T)-
73/06/29
73/07/30
CPU>-
73/07/30
73/08/31
CP(T>-
73/08/31
73/09/28
CP(T>-
73/U9/28
73/10/31
CP(T>-
73/10/31
73/12/26
CP(T)-
73/13/28
74/01/31
CP(T>-
74/01/31
74/02/2R
CPIT1-
74/02/2H
74/04/01
CP-
74/04/01
74/05/31
CP(T>-
74/u5/31
00630
TIME DEPTH N02&N03
Of N-TOTAL
DAY FEET MG/L
11 00
0.193
15 35
11
16
11
16
11
16
11
15
11
16
11
16
11
Ib
11
16
11
16
10
14
10
15
00
00
00
00
00
00
00
00
00
00
00
00
30
30
00
00
00
00
00
00
00
on
0.165
0.095
0.140
0.230
U.020
0.420
0.200
0.200
0.240
0.120
00625
TOT KJEL
N
MG/L
21.800
18.
17.
23.
23.
23.
21.
IB.
17.
16.
17.
ia.
900
600
100
100
000
000
300
000
000
000
000
00610 00671 00665 50051 50053
NH3-N PHOS-DIS PHOS-TOT FLOW CONDUIT
TOTAL ORTHO HATE FLOw-MGD
MG/L MG/L P MG/L P INST MGD MONTHLY
0.370 3. 450 4.940 4.620
C
1
0
0
0
0
0
0
0
0
0
.850
.370
.086
.020
.770
.050
.040K
.060
.050K
.270
.050
0.540
0.550
0.630
0.280
0.870
0.350
0.400
0.790
0.860
0.840
0.840
2.700
2.700
3.900
3.400
3.500
2.500
3.000
4.400
3.150
2.800
2.400
4.990
2.000
4.760
4.270
3.300
4.400
4.500
4.800
4.600
4.400
4.900
4.900
4.400
4.100
4.120
3.700
3.500
4.000
3.900
4.100
J.700
4.600
K, VALUE KNOWN TU BE
LESS THAN INDICATED
-------
STORET RETRIEVAL DATE 76/07/22
011221 TF011221 P070000
34 31 00.0 084 57 00.0 4
CALHOUN (GEORGIA)
01 1:250000 HUME
T/WE1SS RESERVOIR 033591
OOSTANAULA RIVER
11EPALES 2141204
0000 FEET DEPTH CLASS 00
DATE
FROM
TO
73/05/13
73/06/13
73/07/16
73/08/1S
73/09/11
73/10/12
73/11/13
73/12/13
74/01/1*
74/02/10
74/03/13
74/04/1^
74/05/14
00630
TIME DEPTH N02&N03
OF N-TOTAL
DAY FEET MG/L
10 00 1.050
10 00 0.071
10 00 9.700
10 00
10
10
10
10
10
10
10
10
10
00
00
00
00
00
00
00
00
00
0
0
0
1
0
0
0
.110
.390
.180
.120
.160
.280
.200
00625
TOT KJEL
N
MG/L
6.400
7.700
2.200
9.400
6.800
18.000
19.000
3. SCO
8.600
2.300
13.000
00610
NH3-N
TOTAL
MG/L
0.068
0.530
0.260
1.840
2.200
2.200
0.920
0.220
0.280
0.220
0.290
00671 00665 50051
PHOS-DIS PHOS-TOT FLOW
ORTHO RATE
MG/L P MG/L P INST MOD
1.100 2.100
11.000 19.300
11.600 14.500
5.500
14.000
17.300
13.700
11.600
* 2.240
13.200
4.900
10.500
15.
17.
18.
16.
3.
16.
6.
12.
500
300
200
900
400
800
500
bOO
5.410
6. ICO
5.450
4.690
5.230
5.570
4.600
3.420
4.340
50053
CONDUIT
FLOw-MGD
MONTHLY
5.000
5.500
11.600
7.260
3.670
4.750
3.810
-------
APPENDIX E
PARAMETRIC RANKINGS OF LAKES
SAMPLED BY NES IN 1974
STATE OF ALABAMA
-------
LAKE DATA TO BE USEU IN RANKINGS
LAKE
CODE LAKE NAME
OjOl BANKHEAD LAKE
0103 GANTT 3ESERVOIW
0104 GUNTERSVILLE RESERVOIR
0105 HOLT LOCK AND 0AM
0106 LAY LAKE
0107 MARTIN LAKE
010* MITCHELL LAKE
0109 PICKWICK LAKE
0113 WEISS RESERVOIR
0114 WILSON LAKE
0115 LAKE PURDY
MEDIAN
TOTAL P
0.029
0.029
0.044
0.018
0.076
0.017
0.053
0.056
0.092
0.053
0.049
MEDIAN
INORG N
0.770
0.300
0.480
0.835
0.390
0.170
0.290
0.535
0.260
0.460
0.170
500-
MEAN SEC
452.667
465.778
461.111
449.417
470.778
435.250
466.000
455.000
478.389
447.714
437.889
MEAN
CrILORA
4.017
2.144
8.567
2.183
7.056
6.407
6.211
2.450
11.261
7.400
12.711
lii-
MlN 00
14.900
14.000
12.200
13.600
13.000
15.000
12.400
11.900
14.900
10.200
15.000
MEOIAN
DISS ORTrlO
0.007
0.008
0.014
0.006
0.032
0.004
0.022
0.035
0.034
0.022
0.014
-------
PERCENT or LAKES WITH HIGHER VALUES (NUMBER OF LAIVES WITH HIGHER VALUES)
LAKE
CODE LAKE NAME
0101 8ANKHEAD LAKE
0103 GANTT RESERVOIR
010** GUNTERSVILLE RESERVOIR
0105 HOLT LOCK AND DAM
0106 LAY LAKE
0107 MARTIN LAKE
0108 MITCrlELL LAKE
0109 PICKWICK LAKE
0113 WEISS RESERVOIR
0114 WILSON LAKE
0115 LAKE PIJRDY
MEDIAN
TOTAL P
75 (
75 (
60 (
90 (
10 (
100 (
40 (
20 (
0 (
30 (
50 (
7)
7)
6)
9)
1)
10)
4)
2)
0)
3)
5)
MEDIAN
INORG
10 (
60 (
30 (
0 (
50 (
95 (
70 (
20 (
80 (
40 (
95 (
N
1)
6)
3)
0)
5)
9)
7)
2)
8)
4)
9)
500-
MEAN SEC
60 (
30 (
40 (
70 <
10 (
100 (
20 <
50 (
0 (
80 (
90 (
6)
3>
4)
7)
1)
10)
2)
5)
0)
«)
9)
MEAN
CHLOKA
70 (
100 (
20 (
90 (
40 (
50 (
60 (
80 (
10 (
30 (
0 (
7)
10)
2)
9)
4)
5)
6)
8)
1)
3)
0)
15-
MIN i
25 (
40 (
80 (
50 (
60 (
5 (
70 (
90 (
25 (
100 (
5 (
)0
^>
4)
8)
5)
6)
0)
7)
9)
2)
10)
0)
MEDIAN
DISS OKTHO P
80 (
70 (
55 (
90 (
20 (
100 (
35 (
0 (
10 (
35 (
55 (
8)
7)
5)
9)
2)
10)
3)
0)
1)
3)
5)
INDEA
NO
32U
375
265
390
190
450
29S
260
125
315
295
-------
LAKES RANKED BY INDEX NOS.
RANK LAKE CODE LAKE NAME INDEX NO
1 0107 MARTIN LAKE 450
2 0105 HOLT LOCK AND DAM 390
3 0103 GANTT RESERVOIR 375
4 0101 BANKHEAD LAKE 320
5 0114 KILSON LAKE 315
fe 0115 LAKE PURDY 295
7 0108 MITCHELL LAKE 295
8 0104 GUNTERSVILLE RESERVOIR 285
9 0109 PICKWICK LAKE 260
10 0106 LAY LAKE 190
11 0112 WEISS RESERVOIR 125
------- |