U.S. ENVIRONMENTAL PROTECTION AGENCY
NATIONAL EUTROPHICATION SURVEY
WORKING PAPER SERIES
REPORT
ON
MARTIN LAKE
ELMORE AND TALLAPOOSA COUNTIES
ALABAM
EPA REGION IV
WORKING PAPER No, 231
CORVALLIS ENVIRONMENTAL RESEARCH LABORATORY - CORVALLIS, OREGON
and
ENVIRONMENTAL MONITORING & SUPPORT LABORATORY - LAS VEGAS, NEVADA
•&G.P.O. 699-440
-------
REPORT
ON
MARTIN LAKE
ELMORE AND TALLAPOOSA COUNTIES
ALABAMA
EPA REGION IV
WORKING PAPER No, 231
WITH THE COOPERATION OF THE
ALABAMA WATER IMPROVEMENT COMMISSION
AND THE
ALABAMA NATIONAL GUARD
JULY 1976
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CONTENTS
Page
Foreword i -,-
List of Study Lakes - Alabama iv
Lake and Drainage Area Map v
Sections
I. Conclusions -|
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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11
FOREWORD
The National Eutrophicatlon Survey was Initiated 1n 1972 1n
response to an Administration commitment to Investigate the nation-
wide threat of accelerated eutrophication to freshwater lakes and
reservoir-s.
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
[§303(c)L clean lakes [§314(a,b)], and water quality monitoring
[§106 and §305(b)] activities mandated by the Federal Water
Pollution Control Act Amendments of 1972.
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m
Beyond the single lake analysis, broader based correlations
between nutrient concentrations (and loading) and trophic 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 Williford, 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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3/00' —I
MARTIN LAKE
Tributary Sampling Site
X Lake Sampling Site
Sewage Treatment Facility
Drainage Area Boundary
CLEBURNE Co. _
RANDOLPH Co
5 i> / CARROLL Co.
RANDOLPH Co. \_
CHAMBERS Co
33" 30' —\
33° 00'—H
85'00'
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REPORT ON MARTIN LAKE, ALABAMA
STORET NO. 0107
I. CONCLUSIONS
A. Trophic Condition*:
On the basis of field observations and Survey
data, Martin Lake is considered mesotrophic. Moderate
numbers of pollution-tolerant genera were predominant
among the phytoplankton identified. Of the 11 Alabama
lakes sampled in 1973, 10 had higher median total
phosphorus concentrations than Martin Lake, and 9 had
higher median inorganic nitrogen. Chlorophyll a_ levels
ranged from a low of 1.4 yg/1 in the early spring to
27.3 yg/1 in the summer. Secchi disc visibility and
potential for primary production as measured by algal
assay control yield were low. No visible algal blooms
or aquatic macrophytes were reported by field limnologists,
B. Rate-Limiting Nutrient:
Algal assay results indicate that Martin Lake was
limited by available phosphorus levels. Spikes with
phosphorus, and nitrogen and phosphorus simultaneously
result in increases in assay yield. Addition of nitrogen
alone did not stimulate a growth response. The ratios of
inorganic nitrogen to orthophosphorus (N/P) in sampled
waters substantiate phosphorus limitation for all four
sampling rounds.
*See Appendix E.
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C. Nutrient Controllability:
1. Point sources -
The mean annual phosphorus load from point sources
was estimated to be 29.0% of the total load reaching
Martin Lake. Of that load, Alexander City contributed
a total of 26.5% from five wastewater treatment plants.
The remaining three known point sources contributed
2.5% of the total load.
The present loading of 1.35 g P/nr/yr is slightly
above the eutrophic level proposed by Vollenweider for
lakes with such volume and retention time. However,
Vollenweider's oligotrophic and eutrophic levels may
be too low for southeastern piedmont reservoirs
(including Martin Reservoir) which receive heavy sediment
loading, since sediments effectively combine with nutrients-
(nitrates and phosphates) making them unavailable for
biological activity (Raschke 1975).
2. Nonpoint sources -
The mean annual phosphorus load from nonpoint sources
was about 71.0% of the total reaching Martin Lake. The
Tallapoosa River contributed 58.9% of the total load, and
ungaged drainage areas were estimated to have contributed
4.0%.
-------
Regardless of the primary nutrient limitation
suggested by either algal assay or nutrient ratios, the
most feasible approach to nutrient control, if desirable,
is through available phosphorus control technology and
subsequent establishment of phosphorus limitation within
the water body. In Martin Lake, it would be expected
that removal of the known point sources would result in
further improvement of water quality.
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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 data were provided by the Alabama
District Office of the U.S. Geological Survey (USGS) (out-
let 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 are
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:
P
1. Surface area: 157.83 knr
2. Mean depth: 12.9 meters.
3. Maximum depth: 37.0 meters.
4. Volume: 2,036.007 x 10^ m3.
5. Mean hydraulic retention time: 176 days.
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B. Tributary and Outlet (see Appendix B for flow data):
1 . Tributaries -
, Drainage Mean flow
Name area(knr) (m
A(l) Tallapoosa River 5,273.2 83.17
B(l) Emuckfaw Creek 173.0 3.22
C(l) Timbergut Creek 40.1 0.71
D(l) Hillabee Creek 735.6 12.31
E(l) Elkahatchee Creek 86.5 0.97
F(l) Buck Creek 51.0 1.30
6(1) Sandy Creek (north 404.0 7.34
and south forks)
H(l) Oakachoy Creek 43.2 0.32
Minor tributaries and
immediate drainage - 709.8 14.20
Totals 7,516.4 123.54
2. Outlet - A(2) Tallapoosa R. 7,674.2 133.88
C. Precipitation:
1. Year of sampling: 188.4 cm.
2. Mean annual: 141.3 cm.
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III. LAKE WATER QUALITY SUMMARY
Martin Lake 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 seven stations on the lake and from a number
of depths at each station (see map, page v). During each
visit, depth-integrated samples were collected from each sta-
tion for chlorophyll ^analysis and phytoplankton identifica-
tion and enumeration. During the first visit, an 18.9-liter
depth-integrated sample was composited for algal assays. Maxi-
mum depths sampled were 29.0 meters at Station 1, 29.0 meters
at Station 2, 29.3 meters at Station 3, 35.1 meters at Station
4, 27.4 meters at Station 5, 18.3 meters at Station 6, and 19.8
meters at Station 7. 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 phyto-
plankton 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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MASTIN LAKE
STOHET CODE 0107
PHYSICAL AND CHEMICAL CHARACTEKISTICS
PARAMETER
N*
( 3/19/73 )
S«»» = 7
RANGE MEDIAN
MAX
DEPTH
RANGE
(METEKS)
N*
( 6/16/73
S*»» = 7
RANGE MEDIAN
)
MAX
DEPTH
RANGE
(METERS)
N*
( 8/25/73
S*«» = 7
RANGE MEDIAN
)
MAX
DEPTH
RANGE
(METERS)
TEMPERATURE (DEO CENT)
0.-1.5 M DEPTH
MAX DEPTH**
12
7
13.0- 16.8
9.7- 12.0
15.1
11.2
0.0- 1.2
9.1- 29.0
12
7
21.5- 30.5
16.2- 19. b
28.8
17.5
0.0- 1.5
16.8- 29.0
7
7
28.4- 29.6
18.0- 22.3
29.2
19.8
0.0-
15.2-
0.0
29.3
DISSOLVED OXYGEN (MG/L)
0.-1.5 M DEPTH
MAX DEPTH**
CONDUCTIVITY (UMHOS)
0.-1.5 M DEPTH
MAX DEPTH**
fH (STANDARD UNITS)
0.-1.5 M DEPTH
MAX DEPTH**
S
7
12
7
12
7
9.6- 10.1
9.1- 9.8
50.- 50.
50.- 50.
7.3- 7.6
7.1- 7.5
10.0
9.6
50.
50.
7.4
7.4
1.2- 1.2
9.1- 29.0
0.0- 1.2
9.1- 29.0
0.0- 1.2
9.1- 29.0
5
7
12
7
12
7
8.4- 9.2
0.2- 4.5
50.- 50.
50.- 50.
7.5- 8.4
7.1- 7.4
8.8
2.8
50.
50.
7.9
7.3
1.5- 1.5
16.8- 29.0
0.0- 1.5
16.8- 29.0
0.0- 1.5
16.8- 29.0
7
7
7
7
7
7
7.2- 7.6
0.0- 0.4
32.- 43.
33.- 70.
6.8- 7.7
5.8- 6.5
7.4
0.1
38.
48.
7.0
6.1
0.0-
15.2-
0.0-
15.2-
0.0-
15.2-
0.0
29.3
0.0
29.3
0.0
29.3
TOTAL ALKALINITY (MG/L)
O.-l.b M DEPTH
MAX .DEPTH**
TOTAL P (MG/L)
0.-1.5 M DEPTH
MAX DEPTH**
12
7
12
7
10.- 11.
10.- 10.
0.017-0.028
0.012-0.045
10.
10.
0.020
0.021
0.0- 1.2
9.1- 29.0
0.0- 1.2
9.1- 29.0
12
7
12
7
7.- 19.
11.- 19.
0.009-0.027
0.008-0.053
12.
13.
0.014
0.017
0.0- 1.5
16.8- 29.0
0.0- 1.5
16.8- 29.0
7
7
7
7
11.- 15.
13.- 27.
0.007-0.027
0.008-0.068
13.
14.
0.009
0.014
0.0-
15.2-
0.0-
15.2-
0.0
29.3
0.0
29.3
DISSOLVED ORTHO P (Mr,/L)
0.-1.5 M DEPTH
MAX DEPTH**
N02»N03 (MG/L)
0.-1.5 M DEPTH
MAX DEPTH**
AMMONIA (MG/L)
0.-I.5 M DEPTH
MAX DEPTH**
KJELDAHL N (MG/L)
O.-l.b M DEPTH
MAX DEPTH**
SECCHI DISC (METERS)
12
7
12
7
12
7
12
7
7
0.002-0.006
0.003-0.016
0.120-0.220
0.130-0.260
0.040-0.070
0.030-0.070
0.200-0.600
0.200-0.200
0.3- 1.4
0.003
0.004
0.145
0.200
0.050
0.050
0.300
0.200
1.2
0.0- 1.2
9.1- 29.0
0.0- 1.2
9.1- 29.0
0.0- 1.2
9.1- 29.0
0.0- 1.2
9.1- 29.0
12
7
12
7
12
7
12
7
7
0.002-0.018
0.002-0.013
0.050-0.120
0.080-0.290
0.050-0.110
0.050-0.250
0.200-0.700
0.200-0.500
1.5- 2.1
0.002
U.005
0.055
0.200
0.075
0.110
0.400
0.300
2.0
0.0- 1.5
16.8- 29.0
0.0- 1.5
16.8- 29.0
0.0- 1.5
16.8- 29.0
0.0- 1.5
16.8- 29.0
7
7
7
7
7
7
7
7
7
0.004-0.018
0.003-0.037
0.030-0.080
0.030-0.250
0.040-0.080
0.020-0.660
0.500-0.800
0.200-1.200
1.4- 2.8
0.006
0.007
0.040
0.050
0.060
0.320
0.500
0.600
2.3
0.0-
15.2-
0.0-
15.2-
0.0-
15.2-
0.0-
15.2-
0.0
29.3
0.0
29.3
0.0
29.3
0.0
29.3
« iM = NO. OF SAMPLES
«• MAXIMUM DEPTH SAMPLED AT EACH SITE
»»» S = NO. OF SITES SAMPLED ON THIS DATE
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MARTIN LAKE
STORET CODE 0107
PARAMETER
TEMPERATURE (DEii
O.-l.b M DEPTH
MAX DEPTH**
DISSOLVED OXYGEN
0.-1.5 M DEPTH
MAX DEPTH"
N*
CEMT)
8
7
(MG/L)
1
7
CONDUCTIVITY (UMHOS)
0.-1.5 M DEPTH 8
MAX DEPTH'* 7
PH (STANDARD UNITS)
0.-1.5 M DEPTH 6
MAX DEPTH"* 7
TOTAL ALKALINITY
0.-1.5 M DEPTH
MAX DEPTH"*
TOTAL P (MG/L)
0.-1.5 M DEPTH
MAX DEPTH**
DISSOLVED ORTHO P
O.-l.b M DEPTH
MAX DEPTH**
N02»N03 (MG/L)
0.-1.5 M DEPTH
MAX DEPTH**
AMMONIA (Mfi/L)
0.-1.5 M DEPTH
MAX DEPTH**
KJELDAHL N (MG/L)
0.-1.5 M DEPTH
MAX DEPTH**
(MG/L)
B
7
a
7
(MG/L)
8
7
8
7
8
b
8
7
( ll/
S*""
RANGE
20.8- 21.5
16.9- 20.7
5.0- 5.0
0.*- 7.8
31.- 40.
32.- 64.
6.6- 7.4
6.6- 7.0
10.- 16.
10.- 20.
0.010-0.036
0.014-0.059
0.004-0.009
0.004-0.010
0.030-0.060
0.020-0.060
0. 070-0. 1?0
0.070-0.700
0.200-0.900
0.200-1.000
1/7J )
= 7
MEDIAN
21.1
20.5
5.0
6.4
32.
37.
6.7
6.7
12.
13.
0.018
0.030
0.006
0.005
0.035
0.030
0.090
0.085
0.300
0.200
PH'
MAX
DEPTH
RANGE
(METERS)
0.0- 1.5
7.6- 35.1
1.5- 1.5
7.6- 35.1
0.0- 1.5
7.6- 35.1
0.0- 1.5
7.6- 35.1
0.0- 1.5
7.6- 35.1
0.0- 1.5
7.6- 35.1
0.0- 1.5
7.6- 35.1
0.0- 1.5
7.6- 35.1
0.0- 1.5
7.6- 35.1
0.0- 1.5
7.6- 35.1
PHYSICAL AND CHEMICAL CHARACTERISTICS
SECCHI OISC (METERS)
0.9- 2.1
1.2
» N = NO. 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
03/13/73
06/16/73
08/25/73
11/01/73
Algal
Dominant Units
Genera per ml
1. Flagellates 1,667
2. Melosira 538
3. Ankistrodesmus 398
4. Cryptomonas 150
5. Dinoflagellates 97
Other genera 86
Total 2,936
1. Anabaena 590
2. Flagellates 197
3. Peridinium 172
4. Unknown filament 148
5. Cyclotella 74
Other genera 147
Total 1,328
1. Anabaena 1,208
2. Dactylococcopsis 1,060
3. Lyngbya 789
4. Staurastrum 468
5. Peridinium 222
Other genera 1,479
Total 5,226
1. Melosira 623
2. Cryptomonas 566
3. Flagellates 397
4. Dactylococcopsis 198
5. Synedra 142
Other genera 877
Total 2,803
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10
2. Chlorophyll a_ -
Sampling Station Chlorophyll a_
Date Number (yg/1)
03/19/73 1 I-4
2
3 1.6
4 1.5
5 1.7
6 2.1
7 2.3
06/18/73 1 7.7
2 11.2
3 13.8
4 12.7
5 9.2
6 16.4
7 27.3
08/25/73 ' 1 7-7
2 7.2
3 6.3
4 5.0
5 4.8
6 4.8
7 4.7
11/01/73 1 5-9
2 2.9
3 2.9
4 1.9
5 2.3
6 2.9
7 4.8
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11
C. Limiting Nutrient Study:
1. Autoclaved, filtered, and nutrient spiked -
Spike(mg/l )
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
Ortho P
Conc.(mg/l )
0.013
0.023
0.033
0.063
0.038
0.063
0.013
Inorganic N
Conc.(mg/l)
0.192
0.192
0.192
0.192
0.692
1.192
1.192
Maximum Yield
(mg/l-dry wt.)
0.1
3.3
5.2
7.0
9.4
20.2
0.1
Filtered and nutrient spiked -
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
capricornutum, i
0.007
0.017
0.027
0.057
0.032
0.057
0.007
yield of the
ndicates that
0.195
0.195
0.195
0.195
0.695
1.195
1.195 '
0.2
4.0
5.4
6.1
10.8
20.0
0.1
assay alga, Selenastrum
the potential for
primary
production in Martin Lake was low at the time of sample
analysis. An increase in yield with the addition of
phosphorus as well as a lack of response when only nitro-
gen was added indicates phosphorus limitation. Maximum
growth potential was achieved with the simultaneous addi-
tion of both phosphorus and nitrogen.
The N/P ratio in the field was about 55/1, indicating
that the lake was phosphorus limited at the time of assay
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12
sample collection. The mean N/P ratio for the entire
sampling year in Martin Lake was 33/1, also indicating
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 the USGS for
the tributary sites nearest the lake.
In this report, nutrient loads for sampled tributaries
were determined by using a modification of the USGS computer
program for calculating stream loadings. Nutrient loads indi-
cated for tributaries are those measured minus known point
source loads, if any.
Nutrient loadings for unsampled "minor tributaries and
immediate drainage" ("II" of USGS) were estimated by using the
mean annual nutrient loads, in kg/km^/year, for Emuckfaw Creek
and Timbergut Creek at Stations B(l) and C(l), and multiplying
the means by the ZZ drainage area in
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14
The operators of the Wadley and Alexander City (Spring
Hill, Sugar Creek, Dobbs Creek, Christian Creek, and Coley
Creek) wastewater treatment plants provided monthly effluent
samples and corresponding flow data. Nutrient loads for the
cities of Camp Hill and Dadeville wastewater treatment plants
were estimated at 1.134 kg P and 3.401 kg N/Capita/year.
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15
A. Waste Sources:
1. Known municipal
Population
Name Served Treatment
Wad ley
Spring Hill 1 ,
(Alexander City)
Sugar Creek 1 ,
(Alexander City)
Dobbs Creek 1 ,
(Alexander City)
Christian Creek 2,
(Alexander City)
Camp Hill
Dadeville Lagoon 1 ,
Dadeville Raw 1 ,
Outfall
Coley Creek . 3,
(Alexander City)
2. Known industial - None
1 . Stabilization pond
2. Trickling filter
3. Activated sludge
4. Untreated
626* 1
500 2
000 1
749 3
300 3
900 1
200*** 1
647 4
000 . 3
Mean Flow Receiving
(m3/d x 103) Water
0.201. Hutton Creek/
Tallapoosa River
1.703 El kahatchee River
17.596 Sugar Creek/
El kahatchee River
2.366 Dobbs Creek/ Sandy
Creek/Hi llabee Creek
2.892 Sandy Creek/
Hi llabee Creek
0.341** South Fork Sandy
Creek
0.454** Sandy Creek
0.623** Sandy Creek
2.941 Coley Creek/
Hi llabee Creek
*1970 Census.
**Estimated at 0.3785 m3/capita/day.
***U.S. EPA, 1971.
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16
B. Annual Total Phosphorus Loading - Average Year:
1.
Inputs -
Source kg P/yr
a. Tributaries (nonpoint load) -
A(l) Tallapoosa River 125,695
B(1) Emuckfaw Creek 2,035
C(l) Timbergut Creek 470
D(l) Hillabee Creek 7,420
E(1) Elkahatchee Creek 190
F(l) Buck Creek 920
G(l) Sandy Creek 2,920
(north and south forks)
H(l) Oakachoy Creek 455
b. Minor tributaries and imme- 8,520
diate drainage (nonpoint load) -
d.
e.
Known municipal STP's -
Wadley
Spring Hill (Alexander City)
Sugar Creek (Alexander City)
Dobbs Creek (Alexander City)
Christian Creek (Alexander
City)
Camp Hill
Dadeville Lagoon
Dadeville Raw Outfall
Coley Creek (Alexander City)
Septic tanks* -
Known industrial - None
2.
3.
f. Direct precipitation** -
Total
Outputs - A(2) Tallapoosa River
Net annual P accumulation -
410
1,625
44,675
2,820
2,015
1,020
1,360
2,615
5,390
30
2,760
213,345
81,110
132,235
58.9
1.0
0.2
3.5
0.1
0.4
1.4
0.2
4.0
0.2
0.8
20.
1.
1.0
0.5
0.6
1.2
2.5
1.3
100.0
*Estimate based on 90 lakeshore residences and 3 camps.
**Estimated (See NES Working Paper No. 175).
-------
17
a. Tributaries (nonpoint load)
A(l ) Tallapoosa River
B(l) Emuckfaw Creek
C(l) Timbergut Creek
D(l) Hillabee Creek
E(l) Elkahatchee Creek
F(l) Buck Creek
G(l) Sandy Creek
(north and south forks)
H(l) Oakachoy Creek
-
1,647,675
50,395
9,890
250,465
24,935
34,955
216,210
6,970
C. Annual Total Nitrogen Loading - Average Year:
1. Inputs -
Source kg N/yr
60.3
1.8
0.4
9.2
0.9
1.3
7.9
0.3
b. Minor tributaries and imme- 190,935 7.0
diate drainage (nonpoint load) -
c. Known municipal STP's -
Wadley 630 <0.1
Spring Hill (Alexander City) 5,045 0.2
Sugar Creek (Alexander City) 86,410 3.2
Dobbs Creek (Alexander City) 6,165 0.2
Christian Creek (Alexander 5,345 0.2
City)
Camp Hill 3,060 0.1
Dadeville Lagoon 4,080 0.1
Dadeville Raw Outfall 7,020 0.3
Coley Creek (Alexander City) 10,320 0.4
d. Septic tanks* - 1,170 <0.1
e. Known industrial - None
f. Direct precipitation** - 170,395
Total 2,732,070
2. Outputs - A(l) Tallapoosa River 3,572,695
3. Net annual N export*** - 840,625
*Estimate based on 90 lakeshore residences and 3 camps.
**Estimated (See NES Working Paper No. 175).
***Export probably due to unknown sources and/or sampling errors,
-------
18
D. Mean Annual Nonpoint Nutrient Export by Subdrainage Area:
Tributary kg P/km?/yr kg N/km2/yr
A(l) Tallapoosa River 24 312
B(l) Emuckfaw Creek 12 291
C(l) Timbergut Creek 12 247
D(l) Hillabee Creek 10 340
E(l) Elkahatchee Creek 2 288
F(l) Buck Creek 18 685
6(1) Sandy Creek (north and 7 535
south forks)
H(l) Oakachoy Creek 11 161
-------
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 Martin Lake 1.35
Vollenweider's eutrophic loading 1.00
Vollenweider's oligotrophic loading 0.50
-------
20
V. LITERATURE REVIEWED
Raschke, R. L. 1975. Personal communication. Environmental
Protection Agency, Surveillance and Analysis Division,
Athens, Georgia.
U.S. EPA. 1971. A 1968 Inventory of Municipal Waste Facilities,
Vol. 4. EPA Publication No. OWP-1. 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. Hydrol. 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
07/32/76
LAKE CODE 0107
MARTIN LAKE
TOTAL DRAINAGE AREA OF LAKE(SO KM) 7674.2
SUB-ORAINAGE
TRIBUTARY AREAISO KM) JAN
FEB
APR
MAY
NORMALIZED FLOWS(CMS)
JUN JUL AUG
SEP
OCT
NOV
DEC
SUMMARY
TOTAL DRAINAGE AREA OF LAKE
SUM OF SUB-DRAINAGE AREAS
7674.2
7674.4
TOTAL FLO* IN
TOTAL FLOW OUT
1488.58
1608.45
MEAN MONTHLY FLOWS AND DAILY FLOWS(CMS)
TRIBUTARY MONTH YEAR MEAN FLOW DAY FLOW DAY
0107A1
FLOW DAY
FLOW
0107A2
3
4
5
6
7
8
9
10
11
12
1
2
3
4
5
6
7
8
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
249.188
276.089
254.852
133.089
64.562
47.431
31.149
43.891
39.077
117.515
288.832
227.951
207.704
228.205
210.876
110.096
53.094
38.936
24.607
36.132
32.196
97.093
238.881
187.684
4
8
16
10
15
5
16
18
11
16
6
5
7
16
9
14
5
15
18
11
15
5
5
102.224
672.525
128.842
169.901
75.748
38.511
. 36.246
38.228
31.432
64.562
215.203 20
219.456 20
485.917
182.927
364.948
96.560
7.646
137.903 16
24.777
81.213
60.825
177.830 20
181.228 20
125.160
219.456
0.991
103.640
181.228
MEAN
0107A1
0107A2
0107B1
0107C1
0107D1
0107E1
0107F1
0107G1
0107H1
0107ZZ
5273.2
7674.2
173.0
40.1
735.6
86.5
51.0
404.0
43.3
867.6
113.55
123.12
3.96
0.85
15.01
1.36
1.81
10.19
0.453
19.96
138.75
151.67
5.80
1.30
22.65
1.81
2.18
12.74
0.623
25.77
161.69
191.90
6.51
1.44
25.49
2.15
2.46
14.72
0.765
29.73
141.58
196.32
6.94
1.53
27.18
2.01
2.44
13.88
0.708
28.03
86.08
141.87
3.40
0.74
13.03
0.96
1.36
7.65
0.311
14.58
58.76
108.43
2.35
0.54
8.78
0.59
0.93
5.10
0.184
9.34
55.93
97.38
1.90
0.40
6.94
0.54
0.85
4.67
0.164
8.50
46.44
102.65
1.25
0.26
4.53
0.34
0.59
3.11
0.096
5.52
33.27
115.19
1.10
0.23
3.96
0.24
0.45
2.41
0.068
4.11
31.86
119.16
1.25
0.26
4.39
0.23
0.45
2.35
0.065
4.11
50.97
127.28
1.44
0.31
S.24
0.51
0.82
4.39
0.153
8.07
82.83
133.49
2.97
0.65
11.33
0.91
1.30
7.22
0.311
13.59
83.16
133.86
3.22
0.71
12.30
0.97
1.30
7.34
0.323
14.20
-------
TRIBUTARY FLOW INFORMATION FOR ALABAMA
07/22/76
LAKE CODE 0107
MARTIN LAKE
MEAN MONTHLY FLOWS AND DAILY FLOWS(CMS)
TRIBUTARY MONTH YEAR MEAN FLOW DAY
OJ07B1
0107C1
0107D1
0107E1
3 73
4 73
5 73
6 73
7 73
8 73
9 73
10 73
11 73
12 73
1 74
2 74
3 73
4 73
5 73
6 73
7 73
8 73
9 73
10 73
11 73
12 73
1 74
2 74
3 73
4 73
5 73
6 73
7 73
8 73
9 73
10 73
11 73
12 73
1 74
2 74
3 73
4 73
5 73
6 73
7 73
8 73
9 73
10 73
11 73
12 73
1 74
2 74
FLOW DAY
FLOW DAY
FLOW
9.345
9.203
9.769
6.060
3.171
2.718
2.067
1.982
2.124
3.426
7.079
6.966
2.180
2.067
2.237
1.359
0.680
0.595
0.453
0.425
0.453
0.736
1.586
1.557
38.228
36.953
39.644
23.786
12.176
10.194
7.702
7.362
7.787
13.026
28.175
27.751
3.681
3.058
2.860
1.642
0.793
0.425
0.229
0.232
0.311
0.736
2.180
2.322
4
8
16
10
15
5
16
18
11
16
5
5
4
7
16
10
15
5
16
18
11
16
5
5
4
8
16
3
15
5
16
18
11
16
6
5
4
28
24
23
5
15
9
15
18
5
2
4.134
18.689
6.230
6.654
2.039
1.303
0.963
0.736
0.906
2.832
8.920 20
3.964 20
0.906
5.947
1.359
1.472
0.425
0.269
0.195
0.181
0.184
0.623
2.039 20
0.878 20
16.084
78.381
24.636
23.361
7.646
4.672
3.455
2.633
3.171
10.760
25.485 20
15.291 20
1.246 25
3.625
2.039
0.991
0.396
0.283
0.193
0.173
0.311
2.973 9
1.218
3.738
7.306
0.821
1.642
14.442
28.883
6.456
2.039
19
0.680
-------
TRIBUTARY FLOW INFORMATION FOR ALABAMA
07/22/76
LAKE CODE 0107
MARTIN LAKE
MEAN MONTHLY FLOWS AND OAILY FLOWS
-------
APPENDIX C
PHYSICAL AND CHEMICAL DATA
-------
STOftET RETRIEVAL DATE 76/07/32
DATE
FROM
TO
73/03/19
73/06/16
73/08/25
73/11/01
TIME
OF
DAY
09 20
09 20
09 20
09 20
09 20
09 20
09 20
09 50
09 50
09 50
09 50
09 50
09 50
09 50
09 50
09 50
09 50
09 50
09 50
12 30
12 30
12 30
12 30
DEPTH
FEET
0000
0004
0015
0035
0055
0075
0095
0000
0006
0015
0030
0045
0058
0000
0015
0024
0032
0050
0062
0000
0005
0015
0025
00010
WATER
TEMP
CENT
13.2
13.0
13.0
12.7
11.8
10.2
9.7
28.5
27.1
23.1
22.5
20.7
19.8
28.4
28.3
27.5
25.6
21.8
20.4
21.0
20.8
20.6
20.6
010701
32 52 00.0 085 54 30.0 3
MARTIN LAKE
01123 ALABAMA
033491
11EPALES
2111202
0062 FEET DEPTH CLASS
00300
DO
MG/L
10.0
9.9
10.0
9.8
9.6
9.6
9.2
6.3
5.8
3.6
2.8
7.6
2.2
C.I
0.1
5.0
7.2
7.0
00077 00094
TRANSP CNOUCTVY
SECCHI FIELD
INCHES MICROMHO
40 50K
50K
50K
50K
50K
50K
50K
60 50K
50K
50K
50K
50K
50K
54 43
44
43
47
58
67
60 40
40
40
40
00400
PH
SU
7.40
7.50
7.50
7.50
7.50
7.40
7.50
7.60
8.00
7.80
7.60
7.30
7.20
7.50
6.60
6.60
6.50
7.40
7.20
7.10
7.00
00410
T ALK
CAC03
MG/L
10
10K
10K
10K
10K
10K
10K
11
9
12
12
12
13
15
13
18
21
16
14
13
13
00610
NH3-N
TOTAL
MG/L
0.070
0.040
0.050
0.040
0.050
0.060
0.050
0.110
0.080
0.140
0.110
0.220
0.250
0.050
0.040
0.370
0.660
0.100
0.090
0.100
0.090
00
00625
TOT KJEL
N
MG/L
0.600
0.200
0.200K
0.200K
0.200K
0.200K
0.200K
0.600
0.300
0.200K
0.400
0.400
0.500
0.600
0.300
0.700
1.100
0.200
0.200
0.200K
0.200K
00630
N02&N03
N-TOTAL
MG/L
0.220
0.200
0.200
0.200
0.220
0.260
0.260
0.120
0.090
0.260
0.240
0.210
0.220
0.050
0.200
0.050
0.040
0.060
0.060
0.060
0.060
00671
PHOS-DIS
ORTHO
MG/L P
0.005
0.003
0.003
0.003
0.004
0.009
0.016
0.018
0.012
0.013
0.014
0.024
0.013
0.018
0.008
0.024
0.037
0.008
0.006
0.008
0.005
K VALUE KNOWN TO BE
LESS THAN INDICATED
-------
STORE! RETRIEVAL DATE 76/07/22
DATE
FROM
TO
73/03/19
73/06/16
73/08/25
73/11/01
00665 32217
TIME DEPTH PH05-TOT CHLRPHYL
OF A
DAY FEET
09
09
09
09
09
09
09
09
09
09
09
09
09
09
09
09
09
12
12
12
12
20
?0
?0
20
20
20
PO
50
50
50
50
50
50
50
50
50
50
30
30
30
30
0000
0004
0015
0035
0055
0075
0095
0000
0006
0015
0030
0045
0058
0000
0024
0050
0062
0000
0005
0015
0025
MG/L
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
p
028
025
024
024
023
032
045
027
031
049
042
053
053
027
032
054
068
036
033
036
044
UG/L
1.4
7.7
7.7
5.9
010701
32 52 00.0 085 54 30.0 3
MARTIN LAKE
01123 ALABAMA
033491
11EPALES
0062 FEET
DEPTH
2111202
CLASS 00
-------
STORET RETRIEVAL DATE 76/07/22
00010
DATE TIME DEPTH WATER
FROM OF TEMP
TO DAY FEET CENT
73/03/19
73/06/16
73/08/25
73/11/01
10
10
10
10
10
10
10
10
10
10
10
10
10
10
10
10
10
10
10
12
12
12
12
12
12
30
30
30
30
30
30
35
35
35
35
35
35
35
25
25
25
25
25
25
10
10
10
10
10
10
0000
0004
0015
0025
0050
0075
0000
0006
0015
0030
0045
0060
0076
0000
0015
0024
0035
0055
0075
0000
0010
0030
0060
0080
0095
14.
13.
13.
13.
12.
10.
28.
28.
23.
21.
20.
19,
17.
28,
28.
28,
24,
21,
19,
21,
21,
21,
20,
20,
19,
,9
.8
,4
,0
.0
,2
.0
,1
.8
,9
,7
.1
.4
.6
.4
,3
.6
.3
.8
.5
.0
.0
.9
.0
.5
10
9
10
9
9
9
6
5
5
4
4
7
6
0
1
0
7
6
6
6
6
.1
.8
.0
.8
.6
.1
.0
.1
.1
.9
.5
.4
.2
.1
.0
.4
.2
.8
.6
.4
.4
010702
32 49 00.0 085 53 45.0 3
MARTIN LAKE
01123 ALABAMA
033491
11EPALES 2111202
0080 FEET DEPTH CLASS 00
00300
DO
MG/L
10.1
9.8
10.0
9.8
9.6
9.1
6.0
5.1
5.1
4.9
4.5
7.4
6.2
0.1
1.0
0.4
7.2
6.8
6.6
6.4
6.4
00077 00094
TRANSP CNDUCTVY
SECCHI FIELD
INCHES MICROMHO
11 50K
50K
50K
50K
50K
50K
60 50K
50K
50K
50K
50K
50K
50K
84 38
37
38
40
32
34
36 36
36
36
36
38
37
00400
PH
SU
7.50
7.50
7.50
7.50
7.40
7.40
8.40
8.50
8.00
7.70
7.60
7.50
7.30
7.00
6.60
6.00
5.90
5.90
6.90
6.90
6.90
6.70
6.60
6.60
00410
T ALK
CAC03
MG/L
10K
10K
10K
10K
10
10K
7
7
9
8
8
10
11
12
11
15
10
13
11
10
11
12
14
16
00610
NH3-N
TOTAL
MG/L
0.050
0.050
0.050
0.050
0.050
0.070
0.070
0.070
0.080
0.140
0.140
0.100
0.110
0.040
0.030
0.050
0.040
0.060
0.120
0.110
0.120
0.120
0.110
0.100
00625
TOT KJEL
N
MG/L
0.400
0.200
0.200K
0.200K
0.200K
0.200K
0.400
0.200
0.200
0.200
0.200
0.200
0.200K
0.500
0.400
0.300
0.300
0.400
0.400
0.200
0.200K
0.200
0.300
0.300
00630
N02&N03
N-TOTAL
MG/L
0.170
0.170
0.170
0.180
0.200
0.260
0.070
0.070
0.170
0.230
0.200
0.240
0.290
0.030
0.040
0.060
0.230
0.250
0.060
0.060
0.060
0.060
0.050
0.060
00671
PHOS-DIS
ORTHO
MG/L P
0.006
0.004
0.004
0.004
0.004
0.007
0.003
0.004
0.005
0.012
0.007
0.009
0.009
0.016
0.006
0.004
0.010
0.005
0.004
0.007
0.005
0.007
0.007
0.005
K VALUE KNOWN TO BE
LESS THAN INDICATED
-------
STORET RETRIEVAL DATE 76/07/22
DATE
FROM
TO
73/03/1Q
73/06/16
73/08/25
73/11/01
00665 32217
TIME DEPTH PHOS-TOT CHLRPHYL
OF A
JAY FEET
10
10
10
10
10
10
10
10
10
10
10
10
10
10
10
10
10
10
12
12
12
12
12
12
30
30
30
30
30
30
35
35
35
35
35
35
35
25
?5
25
25
?5
10
10
10
10
10
10
0000
0004
0015
0025
0050
0075
0000
0006
0015
0030
0045
0060
0076
0000
0024
0035
0055
0075
0000
0010
0030
0060
0080
0095
MG/L P
0
0
0
I
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
u
0
0
0
.020
.019
.018
.019
.020
.029
.023
.025
.033
.042
.040
.031
.030
.015
.015
.022
.016
.021
.023
.022
.027
.028
.062
.059
UG/L
11.2
7.2
2.9
010702
32 49 00.0 085 53 45.0 3
MARTIN LAKE
01123 ALABAMA
033491
11EPALES 2111202
0080 FEET DEPTH CLASS 00
-------
STORET RETRIEVAL DATE 76/07/22
DATE
FROM
TO
73/03/19
73/06/18
73/08/25
73/11/01
TIME
OF
DAY
11
11
11
11
11
10
10
10
10
10
10
10
10
12
12
12
12
12
12
11
11
11
11
15
15
15
15
15
10
10
10
10
10
10
10
10
40
40
40
40
40
40
50
50
50
50
DEPTH
FEET
0000
0004
0015
0030
0040
0000
0005
0015
0020
0030
0050
0065
0080
0000
0015
0030
0045
0070
0096
0000
0010
0025
0040
00010
WATER
TEMP
CENT
15.4
14.8
14.0
12.3
11.5
28.9
28.6
27.4
24.4
21.5
20.2
19.0
17.2
29.2
28.6
27.1
22.5
20.1
18.0
21.3
20.8
20.7
20.7
010703
32 44 40.0 385 50 35.0 3
MARTIN LAKE
01123 ALABAMA
033491
11EPALES . 2111202
0085 FEET DEPTH CLASS 00
00300
DO
MG/L
9.9
9.6
9.7
9.7
8.4
8.4
6.2
4.1
4.3
3.6
1.8
7.2
6.8
0.1
0.1
U.I
0.1
7.4
7.2
7.0
00077
TRANSP
SECCHI
INCHES
48
66
80
36
00094
CNDUCTVY
FIELD
MICROMHO
50K
50K
50K
50K
50K
50K
50K
50K
50K
50K
50K
50K
50K
38
37
40
38
39
70
32
32
32
32
00400
PH
SU
7.30
7.60
7.40
7.40
7.50
8.00
8.10
7.70
7.30
7.30
7.20
7.20
7.10
6.80
6.40
5.90
5.90
5.90
6.30
6.80
6.80
6.80
6.80
00410
T ALK
CAC03
MG/L
10K
10
10
10
10
12
13
13
16
14
15
14
17
13
11
14
14
15
27
12
11
11
11
00610
NH3-N
TOTAL
MG/L
0.050
0.050
0.030
0.040
0.030
0.070
0.060
0.070
0.080
0.100
0.070
0.140
0.090
0.060
0.040
0.040
0.100
0.120
0.620
0.070
0.080
0.080
0.030
00625
TOT KJEL
N
MG/L
0.400
0.200
0.200K
0.200
0.200K
0«700
0.300
0.200
0.200K
0.200K
0.300
0.200
0 = 400
0.600
0.500
0.300
0.400
0.400
1.200
0.300
0.200K
0.200K
0.200K
00b30
N02&N03
N-TOTAL
MG/L
0.140
0.150
0.160
0.180
0.190
0.050
0.050
0.060
0.060
0.150
0.130
0.220
0.200
0.060
0.040
0.060
0.040
0.020
0.050
0.030
0.040
0.030
0.030
00671
PHOS-DIS
ORTHO
MG/L P
0.003
0.002
0.003
0.003
0.003
0.002K
OoOOZK
0.002K
Oo002K
0.002K
Oo002K
0.002
0.005
0.006
0.005
0.006
0.009
0.007
0.006
0.005
0.013
0.006
0.004
K VALUE KNOWN TO BE
LESS THAN INDICATED
-------
STORE! RETRIEVAL DATE 76/07/22
DATE
FROM
TO
73/03/19
73/06/18
73/08/25
73/11/Oi
00665 32217
TIME DEPTH PHOS-TOT CHLRPHYL
OF A
DAY FEET
11
11
11
11
11
10
10
10
10
10
10
10
10
12
12
12
12
12
12
11
11
11
11
15
15
15
15
15
10
10
10
10
10
10
10
10
40
40
40
40
40
40
50
50
50
50
0000
0004
0015
0030
0040
0000
0005
0015
0020
0030
0050
0065
0080
0000
0015
0030
0045
0070
0096
0000
0010
0025
0040
MG/L P
0.018
0.017
0.017
0.018
0.019
0.017
0.015
0.022
0.011
0.011
0.012
0.009
0.017
0.011
0.013
0.014
0.010
0.009
0.024
0.013
0.019
0.018
0.016
UG/L
1.6
13.8
6.3
2.9
010703
32 44 40.0 085 50 35.0 3
MARTIN LAKE
01123 ALABAMA
033491
11EPALES
0085 FEET
2111202
DEPTH CLASS 00
-------
STORE! RETRIEVAL DATE 76/07/32
010704
32 44 fO.O 085 50 35»0 3
MARTIN LAKE
01123 ALABAMA
033491
11EPALES 2111202
0100 FEET DEPTH CLASS 00
DATE
FROM
TO
73/03/19
73/06/18
73/08/25
73/11/01
TIME DEPTH
OF
DAY FEET
13 40 0000
13 40 0008
13 40 0015
13 40 0030
13 30 0000
13 30 0005
13 30 0015
13 30 0030
13 30 0050
13 30 0075
13 30 0095
13 40 0000
13 40 0015
13 40 0030
13 40 0045
13 40 0060
13 40 0081
11 20 0000
11 20 0010
11 20 0030
11 20 0060
11 20 0080
11 20 0100
11 20 0115
00010
WATER
TEMP
CENT
14.8
14.4
14.0
11.5
29.7
29.2
27.5
21.3
20.3
17.8
16.2
29.3
28.9
28.3
23.1
20.9
19.5
21.5
21.3
21.3
21.3
20.5
18.5
16.9
00300
DO
MG/L
9.6
10.1
9.5
8.8
8.7
4.5
4.8
4.6
4.2
7.6
7.2
7.2
0.1
0.5
0.4
6.4
5.6
5.8
0.4
0.4
0*4
00077
TRANSP
SECCHI
INCHES
52
80
90
84
00094
CNUUCTVY
FIELD
MICROMHO
50K
50K
50K
50K
50K
50K
50K
50K
50K
50K
50K
32
35
35
33
32
33
31
31
31
31
43
58
64
00400
PH
SU
7.40
7.50
7.50
7.50
7.70
8.30
8. 1C
7.70
7.60
7.50
7.40
7.70
6.90
6.20
5.80
5.70
5.80
6.60
6.60
6.50
6.50
6.50
6.50
6.60
00410
T ALK
CAC03
MG/L
11
10K
10K
10K
10K
10K
10K
10K
10K
11
11
13
12
12
13
13
14
13
10
14
17
18
23
20
00610
NH3-N
TOTAL
MG/L
0.050
0.040
0.050
0.050
0.090
0.050
0.100
0.090
0.090
0.060
0.050
0.060
0.060
0.060
0.050
0.050
0.020
0.090
0.080
0.080
0.070
0.270
0.690
0.700
00625
TOT KJEL
N
MG/L
0.400
0.200
0.200K
0.200K
0.400
0.300
0.400
0.200K
0.200K
0.200K
0.200K
0.800
0.500
0.500
0.200K
0.200K
0.200K
0.400
0.200
0.200
0.200K
0.500
0.900
1.000
00630
N02&N03
N-TOTAL
MG/L
0.120
0.120
0.120
0.140
0.070
0.050
0.090
0.160
0.190
0.210
0.220
Oo040
0.060
0.020
0.120
0.160
0.170
0.030
0.020
0.030
0.020
0.030
0.030
0.040
00671
PHOS-DIS
ORTHO
MG/L P
0.004
0.003
0.002
0.003
0.012
0.013
0.009
0.007
0.007
0.005
0.006
0.004
0.003
0.004
0.003
0.003
0.003
0.006
0.006
0.004
0.004
0.004
0.004
0.005
K VALUE KNOWN TO BE
LESS THAN INDICATED
-------
STORE! RETRIEVAL DATE 76/07/22
DATE
FROM
TO
73/03/19
73/06/18
73/08/25
73/11/01
00665 32217
TIME DEPTH PHOS-TOT CHLRPHYL
OF A
DAY FEET MG/L P
13
13
13
13
13
13
13
13
13
13
13
13
13
13
13
13
13
11
11
11
11
11
11
11
40
40
40
40
30
30
30
30
30
30
30
40
40
40
40
40
40
20
?0
20
20
20
?0
20
0000
0008
0015
0030
0000
0005
0015
0030
0050
0075
00^5
0000
0015
0030
0045
0060
0081
0000
0010
0030
0060
0080
0100
0115
0.020
0.015
0.013
0.012
0.014
0.016
0.024
0.020
0.027
0.013
0.010
0.009
0.009
0.008
0.008
0.008
0.008
0.013
0.010
0.011
0.011
0.022
0.024
0.033
UG/L
1.5
12.7
5.0
1.9
010704
32 44 40.0 035 50 35.0 3
MARTIN LAKE
01123 ALABAMA
033491
HEPALES
0100 FEET
2111202
DEPTH CLASS 00
-------
STOKET RETRIEVAL DATE 76/07/22
DATE
FROM
TO
73/03/19
73/06/18
73/08/25
73/11/01
00010
TIME DEPTH WATER
OF TEMP
DAY FEET
14
14
14
14
14
14
14
14
14
14
14
14
14
14
14
14
14
14
14
14
09
09
09
09
09
09
15
15
15
15
15
15
25
25
25
25
25
25
25
15
15
15
15
15
15
15
30
30
30
30
30
30
0000
0004
0009
0015
0025
0040
0000
0005
0010
0015
0040
0060
0075
0000
0015
0030
0045
0060
0075
0089
0000
0010
0030
0055
0075
0090
CENT
16
16
16
15
12
11
30
28
28
25
20
19
17
29
28
28
22
20
19
18
21
21
21
21
20
19
.8
.7
.1
.4
.2
.2
.5
.8
.4
.0
.5
.1
.5
.4
.7
.1
.9
.9
.8
.4
.2
.1
.1
.1
.9
.4
00300
DO
MG/L
10
10
9
9
9
9
7
4
4
3
3
7
7
4
0
0
0
0
6
6
6
7
1
.1
.0
.8
.8
.8
.0
.4
.8
.9
.6
.0
.4
.2
.4
.1
.1
.1
.1
.6
.4
.4
.0
.4
010705
32 43 15.0 085 55 55.0 3
MARTIN LAKE
01051 ALABAMA
033491
11EPALES 2111202
0080 FEET DEPTH CLASS 00
00300
DO
MG/L
10.1
10.0
9.8
9.8
9.8
9.0
7.4
4.8
4.9
3.6
3.0
7.4
7.2
4.4
0.1
0.1
0.1
0.1
6.6
6.4
6.4
7.0
1.4
00077 00094
TRANSP CNDUCTVY
SECCHI FIELD
INCHES MICROMHO
54 50K
50K
50K
50K
50K
50K
82 50K
50K
50K
50K
50K
50K
50K
108 38
35
35
35
33
37
48
68 31
32
32
31
32
52
00400
PH
SU
7.40
7.40
7.40
7.40
7.40
7.40
7.70
8.10
8.40
8.10
7.80
7.60
7.40
7.30
6.60
6.10
5.80
5.90
6.00
6.10
6.70
6.70
6.70
6.50
6.50
6.70
00410
T ALK
CAC03
MG/L
10K
10K
10K
12
11
10
11
11
12
12
12
13
14
12
10
10
10
12
13
10K
10K
10K
10K
12
20
00610
NH3-N
TOTAL
MG/L
0.060
0.040
0.040
0.050
0.050
0.050
0.100
0.080
0.070
0.050
0.080
0.050
0.080
0.030
0.060
0.080
0.080
0.150
0.320
0.090
0.090
0.090
0.090
0.150
00625
TOT KJEL
N
MG/L
0.300
0.200
0.200
0.200
0.200K
0.200K
0.400
0.300
0.300
0.200
0.200K
0.200K
0.500
0.300
0.300
0.300
0.300
0.600
0.600
0.300
0.200K
0.200K
0.200
0.400
0.200
00630
N02&N03
N-TOTAL
MG/L
0.140
0.130
0.120
0.140
0.200
0.200
0.050
0.080
0.040
0.040
0.160
0.150
0.080
0.030
0.050
0.040
0.040
0.020
0.030
0.030
0.020
0.020
0.020
0.030
0.020
00671
PHOS-DIS
ORTHO
MG/L P
0.004
0.003
0.002
0.003
0.003
0.003
0.004
0.004
0.002
0.003
0.003
0.002K
0.004
0.009
0.005
0.002
0.002
0.004
0.007
0.005
0.005
0.004
0.004
0.010
0.007
K VALUE KNOWN TO BE
LESS THAN INDICATED
-------
STOPET RETRIEVAL DATE 76/07/22
00665
DATE TIME DEPTH PHOS-TOT
FROM OF
TO DAY FEET MG/L P
73/03/19 14
73/06/18
73/08/25
73/11/01
14
14
14
14
14
14
14
14
14
14
14
14
14
14
14
14
14
14
14
09
09
09
09
09
09
15
15
15
15
15
15
?5
?5
?5
25
?5
25
15
15
15
15
15
15
15
30
30
30
30
30
30
0000
0004
0009
0015
0025
0040
0000
0005
0010
0015
0060
0075
0000
0015
0030
004b
0060
0075
0089
0000
0010
0030
0055
0075
0090
0
0
0
0
0
0
0
0
0
0
0
0
G
0
0
0
0
0
0
0
0
0
0
0
0
.020
.020
.018
.024
.022
.024
.009
.012
.012
.013
.009
.008
.007
.010
.008
.007
.007
.010
.014
.010
.010
.015
.012
.016
.018
32217
CHLRPHYL
A
UG/L
1.7
9.2
4.8
2.3
010705
32 43 15.0 085 55 55.0 3
MART IN LAKL
01051 ALABAMA
033491
11EPALES
0080 FEET
DEPTH
2111202
CLASS 00
-------
STORET RETRIEVAL DATE 76/07/22
DATE
FROM
TO
73/03/19
73/06/18
73/08/25
73/11/01
TIME
OF
DAY
14
14
14
14
14
16
16
16
16
16
16
16
16
16
16
09
09
09
09
50
50
50
50
50
20
20
20
20
20
10
10
10
10
10
10
10
10
10
DEPTH
FEET
0000
0004
0015
0025
0035
0000
0005
0015
0030
0055
0000
0015
0025
0040
0050
0000
0010
0035
0060
00010
WATER
TEMP
CENT
16.1
16.1
15.1
12.9
12.0
21.5
28.6
24.5
21.5
19.4
29.6
29.1
28.8
24.6
22.3
20.9
20.8
20.8
20.5
010706
32 44 15.0 086 01
MARTIN LAKE
01051 ALABAMA
10.0 3
033492
11EPALES 2111202
0060 FEET DEPTH CLASS 00
00300
DO
MG/L
9.6
9.2
9.7
9.1
8.8
10. 8J
4.0
0.2
7.6
6.8
5.0
0.3
0.1
5.2
7.0
5.2
00077
TRANSP
SECCHI
INCHES
32
82
108
48
00094
CNDUCTVY
FIELD
MICROMHO
50K
50K
50K
50K
50K
50K
50K
50K
50K
50K
38
35
35
42
49
32
31
32
32
00400
PH
SU
7.40
7.40
7.40
7.40
7.10
7.50
7.80
7.70
7.50
7.20
6.80
6.5C
6.30
6.00
6.00
6.7Q
6.70
6.7C
6.70
00410
T ALK
CAC03
MG/L
11
11
11
12
10K
14
16
14
14
15
11
11
11
14
16
10K
10
10K
10K
00610
NH3-N
TOTAL
MG/L
0.050
0.050
0.050
0.060
0.060
0.100
0.070
0.060
0.100
0.240
0.060
0.060
0.050
0.130
0.380
0.080
0.080
0.070
0.080
00625
TOT KJEL
M
MG/L
0.300
0.200
0.200K
0.200K
0.200
0.400
0.200
0.200
0.200
0.300
0.500
0.300
0.300
0.400
0.800
0.200
0.200K
0.200
0.200
00630
N02&N03
N-TOTAL
MG/L
0.120
0.120
0.120
0.130
0.130
0.060
0.060
0.050
0.090
0.080
0.040
0.050
0.040
0.030
0.050
0.030
0.030
0.030
0.030
00671
PHOS-DIS
ORTHO
MG/L P
0.003
0.003
0.003
0.002
0.004
0.002K
0.002K
0.002K
0.002
0.002K
0.006
0.005
0.008
0.006
0.008
0.007
0.004
0.005
0.005
KNOWN TO 9F L^SS
THAN INDICATED
J VALIJF KNOWN TO BE
ERROR
-------
STORE! RETRIEVAL DATE 76/07/23
DATE
FROM
TO
73/03/19
73/06/18
73/08/25
73/11/01
00665 32217
TIME DEPTH PHOS-TOT CHLRPHYL
OF A
DAY FEET
14
14
14
14
14
16
16
16
16
16
16
16
16
16
16
09
09
09
09
50
SO
50
50
SO
20
20
?0
20
20
10
10
10
10
10
10
10
10
10
0000
0004
0015
0025
003b
0000
0005
0015
0030
0055
0000
0015
0025
0040
0050
0000
0010
0035
0060
MG/L P
0.023
0.023
0.019
0.014
0.019
0.011
0.014
0.011
0.007
0.029
0.009
0.011
0.011
0.011
0.010
0.013
0.013
0.013
0.014
UG/L
2.1
16.4
4.8
2.9
010706
32 44 15.0 086 01
MARTIN LAKE
01051 ALABAMA
11EPALES
0060 FEET
10.0 3
033492
DEPTH
2111202
CLASS 00
-------
STORET RETRIEVAL DATE 76/07/22
DATE
FROM
TO
73/03/19
73/06/18
73/08/25
73/11/01
00010
TIME DEPTH WATER
OF TEMP
DAY FEET
15
15
15
15
15
17
17
17
17
17
16
16
16
16
16
09
09
09
09
35
35
35
35
35
00
00
00
00
00
40
40
40
40
40
35
35
35
35
0000
0006
0015
0035
0055
0000
0005
0015
0030
0055
0000
0015
0025
0045
0065
0000
0010
0030
0050
CENT
16.2
15.6
14.7
12.8
10.7
29.4
29.1
24.3
21.0
19.2
29.1
28.6
28.3
22.9
20.4
20.9
20.9
20.8
20.7
010707
32 47 30.0 085 59 45.0 3
MARTIN LAKE
01123 ALABAMA
033491
11EPALES 2111202
0060 FEET DEPTH CLASS 00
00300
DO
MG/L
10.0
9.6
9.6
9.4
9.2
8.8
4.8
1.8
7.2
7.0
6.0
0.1
0.0
9.8
7.4
7.8
00077
TRANSP
SECCHI
INCHES
49
83
110
48
00094
CNDUCTVY
FIELD
MICROMHO
50K
50K
50K
50K
50K
50K
50K
50K
50K
50K
38
36
36
37
43
32
32
32
33
00400
PH
SU
7.30
7.30
7.40
7.40
7.30
7.70
8.20
8.00
7.70
7.40
6.90
6.70
6.40
6.00
6.20
6.70
6.70
6.70
6.70
00410
T ALK
CAC03
MG/L
10K
10K
10K
10K
10K
16
19
16
16
19
12
11
12
13
13
10K
10K
10K
10K
00610
NH3-N
TOTAL
MG/L
0.050
0.040
0.050
0.040
0.050
0.090
0.060
0.070
0.070
0.180
0.050
0.070
0.040
0.110
0.300
0.070
0.060
0.070
0.070
00625
TOT KJEL
N
MG/L
0.500
0.200
0.200
0.200K
0.200K
0.500
0.200
0.300
0.200K
0.300
0.500
0.400
0.300
0.300
0.600
0.900
0.200
0.200
0.200K
00630
N02&N03
N-TOTAL
MG/L
0.150
0.140
0.200
0.210
0.230
0.050
0.050
0.050
0.120
0.120
0.040
0.060
0.020
0.020
0.030
0.040
0.030
0.020
0.030
00671
PHOS-DIS
ORTHO
MG/L P
0.004
0.003
0.006
0.003
0.004
0.002K
0.002K
0.002K
0.002K
0.002K
0.004
0.006
0.006
0.008
0.007
0.009
0.007
0.007
0.010
K VALUE KNOKN TO BE
LESS THAN INDICATED
-------
STORET RETRIEVAL DATE 76/07/22
DATE
FROM
TO
73/03/19
73/06/18
73/08/25
73/11/01
00665 32217
TIME DEPTH PHOS-TOT CHLRPHYL
OF A
DAY FEET
15
15
15
15
15
17
17
17
17
17
16
16
16
16
16
09
09
09
09
35
35
35
35
35
00
00
00
00
00.
40
40
40
40
40
35
35
35
35
0000
0006
0015
0035
0055
0000
0005
0015
0030
0055
0000
0015
0025
0045
0065
0000
0010
0030
0050
MG/L P
0.026
0.020
0.020
0.021
0.021
0.014
0.012
0.018
0.011
0.015
0.008
0.008
0.010
0.008
0.009
0.024
0.017
0.023
0.030
UG/L
2.3
27.3
4.7
4.8
010707
32 47 30.0 085 59 45.0 3
MARTIN LAKE
01123 ALABAMA
033491
HEPALES
0060 FEET
DEPTH
2111202
CLASS 00
-------
APPENDIX D
TRIBUTARY AND WASTEWATER
TREATMENT PLANT DATA
-------
STORET RETRIEVAL DATE 76/07/32
0107A1 LS0107A1
32 58 30.0 085 4* 30.0 4
TALLAPOOSA RIVER
01 MAP TALLAPOOSA C
I/MARTIN LAKE 033491
BRDG ON ST RT 49 NEAR HORSESHOE BATTLE G
11EPALES 2111204
0000 FEET DEPTH CLASS 00
DATE
FROM
TO
73/03/04
73/04/08
73/Oii/lb
73/06/10
73/07/15
73/08/05
73/09/16
73/10/18
73/11/11
73/12/16
74/0 I/Ob
7^/01/20
74/02/05
74/02/20
00630 00625
TIME DEPTH N02NN03 TOT KJEL
OF N-TUTAL M
DAY FEET
11
11
13
09
08
09
14
11
10
10
10
08
11
14
10
10
30
45
35
45
15
40
10
10
10
45
00
00
MG/L
0
0
0
f\
-------
STORE! RETRIEVAL DATE 76/07/22
0107A2 LS0107A2
32 40 30.0 085 55 00.0 4
TALLAPOOSA RIVER
01 MAP TALLAPOOSA C
0/MARTIN LAKE 033491
HHY «RDG JUST BELO MARTIN DAM
11EPALHS 2111204
0000 FEET DEPTH CLASS 00
DATE
FROM
TO
73/03/04
73/04/07
73/05/16
73/06/09
73/07/14
73/08/05
73/09/16
73/10/lfl
73/11/11
73/12/15
74/01/05
74/0 l/?0
74/02/05
74/02/20
00630 00625
TIME DEPTH N02&.N03 TOT KJEL
OF N-TOTAL M
UAY FEET
10
15
10
09
14
09
13
09
08
09
09
13
11
13
00
35
00
45
20
45
?5
30
50
05
00
?0
45
00
MG/L
0
0
0
0
0
C
0
0
0
0
0
0
0
0
.170
.176
.168
.132
.147
.180
.040
.015
.017
.120
.168
.19?
.200
.224
MG/L
3.
1.
1.
0.
0.
0.
1.
0.
0.
0.
0.
0.
0.
0.
700
400
300
300
230
210
100
300
300
200
100
100
100K
100K
00610 OC671 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.
098
063
040
020
042
022
069
154
115
032
040
064
040
020
MG/L P
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
016
009
007
005K
005K
006
005K
012
020
005K
005K
OOfl
010
010
MG/L P
0.035
0.025
O.U15
0.025
0.010
0.015
0.010
0.012
0.020
0.010
0.015
0.025
0.020
0.025
K VALUE KNOWN ro BE
LESS THAN INDICATED
-------
STOKET RETRIEVAL DATE 76/07/22
0107dl LS0107B1
33 QO 00.0 OH5 44 30.0 4
EMUCKFAW CREEK
01 MAP TALLAPOOSA C
T/MARTIN LAKE 033491
bRDG UN SECONDARY HWY IN HAMLET
11EPALES 2111204
0000 FEET DEPTH CLASS 00
DATE
FROM
TO
73/03/04
73/04/08
7 3/0 5/ lb
73/06/10
73/07/15
73/08/05
73/09/lb
73/10/18
73/1 1/11
73/12/16
74/01/05
74/01/20
74/02/05
74/02/20
00630 00625
TIME DEPTH N02C.N03 TOT KJEL
OF N-TOTAL M
UAY FEET
11
11
13
09
09
10
11
13
11
09
13
09
10
14
30
?0
35
55
00
05
07
50
10
35
20
05
35
15
MG/L
&
0
0
0
0
0
0
0
0
0
0
0
o
0
.O3a
.065
.054
.048
.064
.052
.063
.017
.010K
.080
.068
.064
.072
.068
MG/L
0.
1.
1.
0.
0.
0.
1.
0.
0.
0.
0.
0.
0.
0.
390
440
50C
170
220
100K
600
100K
250
100K
100
100K
100K
100K
00610 00671 00665
IMH3-N PHOS-DIS PHOS-TOT
TOTAL ORTHO
MG/L
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
p.
a.
0.
025
078
032
008
025
015
147
022
023
032
034
075
C15
030
MG/L
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0 .
0.
p
009
Oil
006
008
006
007
006
005K
015
008
008
005K
005
005K
MG/L P
0.015
0.065
0.020
0.020
O.C20
0.015
0.016
0.025
0.030
0.030
0.025
O.U15
0.015
0.015
K VALUE KNOWN TO BE
LESS THAN INDICATED
-------
STORET RETRIEVAL DATE 76/07/22
0107C1 LS0107C1
32 59 00.0 085 48 30.0 4
TIMBERGUT CREEK
Cl MAP TALLAPOOSA C
T/MARTIN LAKE 033491
BRDG ON RD 1.5 MI SSE OF FOSHEETON
11EPALES 2111204
0000 FEET DEPTH CLASS 00
DATE
FROM
TO
73/03/04
73/04/07
73/05/16
73/06/10
73/07/15
73/08/05
73/09/16
73/10/18
73/11/11
73/12/16
74/01/05
74/01/20
74/02/05
74/02/20
00630 00625
TIME DEPTH N02&.N03 TOT KJEL
OF N-TOTAL N
DAY FEET
12
11
14
10
09
10
10
12
11
09
13
09
11
14
00
4?
00
30
30
55
45
15
20
00
35
20
30
30
MG/L
0
(j
0
0
0
0
0
0
0
0
0
0
0
0
.052
.078
.075
.080
.132
.092
.072
.037
.018
.136
.140
.096
.104
.112
MG/L
1.
0.
C.
0.
1.
0.
0.
0.
0.
0.
0.
0.
0.
0.
800
5?0
200
190
100
100K
220
100K
250
200
100
100K
100K
100K
00610 00671 00665
NH3-N PHOS-DIS PHOS-TOT
TOTAL ORTHO
MG/L
0
0
C
0
0
0
0
0
0
0
0
0
0
0
.058
.024
.014
.015
.075
.015
.019
.037
.066
.020
.016
.016
.010
.020
MG/L P
0
0
0
0
0
0
0
0
0
0
0
0
0
0
.008
.008
.006
.009
.009
.005K
.006
.010
.015
.016
.008
.008
.005
.005K
MG/L P
0.015
0.020
0.011
0.015
0.030
0.015
0.020
0.020
0.065
0.045
0.015
0.010
0.010
C.005
K VALUE KNOWN TO d£
LESS THAN INDICATED
-------
STOREF RETRIEVAL DATE 76/07/22
0107U1 LS0107D1
32 59 00.0 085 51 JO.O 4
HILLABEE CKEEK
01 MAP TALLAPUOSA C
T/MArtTIN LAKE 033491
B*DG ON ST kT 63 2 MI Srt OF FOSnEETON
HE^ALES 2111204
0000 FEET DEPTH CLASS 00
DATE
FROM
TO
73/03/04
73/04/08
73/05/16
73/0&/03
73/07/15
73/08/05
73/09/16
73/10/18
73/11/11
73/12/lb
74/01/06
74/yl/20
74/02/05
74/02/20
00630 00625
TIME DEPTH N02&N03 TOT KJEL
OF N-TOTAL N
DAY FEET
12
11
14
10
09
10
10
12
11
09
09
09
10
15
30
50
30
10
40
40
30
30
35
00
45
30
40
00
MG/L
0
0
0
0
0
0
0
0
0
0
0
0
a
:)
.092
.105
.084
.096
.132
.086
.240
.097
.025
.108
.208
.168
.140
.116
MG/L
0.
2.
0.
0.
0.
0.
2.
0.
0.
0.
0.
0.
0.
0.
520
500
840
210
250
230
150
150
200
100K
600
200
200
100K
00610 00671 00665
NH3-N PHOS-OIS PHOS-TOT
TOTAL ORTMO
MG/L
0.
0.
C.
0.
0.
0.
0.
0.
0.
3.
0.
0.
0.
0.
025
086
016
009
023
015
140
030
Oil
012
080
016
020
010
MG/L
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
p
010
014
006
010
019
010
016
021
018
016
OOfl
012
010
010
MG/L P
0.020
0.095
0.055
0.045
0.060
0.050
0.040
0.050
0.065
0.040
0.050
0.020
0.030
0.020
K VALUE KNOWN TO Be.
LESS THAN INDICATED
-------
STORE! RETRIEVAL DATE 76/07/22
0107E1 LS0107E1
32 53 00.0 085 58 00.0 4
ELKAHATCHEE CREEK
01 MAP TALLAPOOSA C
T/MARTIN LAKE 033491'
dRDG ON ST RT 63 2 Ml S OF ALEXANDER
11EPALES 2111204
0000 FEET DEPTH CLASS 00
DATE
FROM
TO
73/03/04
73/03/25
73/04/28
73/05/24
73/06/23
73/08/05
73/09/15
73/10/09
73/10/15
73/12/18
74/01/05
74/01/09
74/01/19
74/02/02
00630 00625
TIME DEPTH N026.N03 TOT KJEL
OF N-TOTAL N
DAY FEET
16
09
14
12
13
11
09
08
09
09
10
10
10
09
00
05
00
30
00
00
30
15
45
15
45
20
15
45
MG/L
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
023
110
094
015
048
071
048
231
280
184
152
160
136
108
MG/L
0.420
2.720
1.540
1.050
0.320
0.440
0.750
2.600
0.700
0.300
0.300
0.900
0.100K
0.100
00610 00671 OC665
NH3-N PHOS-DIS PHOS-TOT
TOTAL ORTHO
MG/L
0.
1.
0.
0.
0.
0.
G.
0.
0.
0.
G.
0.
0.
0.
027
020
110
035
016
040
030
440
058
090
044
096
030
035
MG/L
0.
0.
p
023
029
0.028
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
021
016
009
013
019
019
010
022
020
025
025
MG/L P
0
0
0
0
0
0
0
0
0
0
0
0
0
.065
.095
.070
.070
.045
.045
.060
.035
.050
.075
.075
.045
.045
K VALUE KNOWN TO BE
LESS THAN INDICATED
-------
STORE! RETRIEVAL DATE 76/07/22
0107F1 LS0107F1
32 48 UO.O 085 47 30.0 4
bUCK CREEK
01 MAP TALLAPOOSA C
T/MARTIN LAKE 033491
8RDG UN RD 1.5 MI SW OF DAOEVILLE
11EPALES 2111204
0000 FEET DEPTH CLASS 00
DATE
FROM
TO
73/03/04
73/04/08
73/05/16
73/06/09
73/07/14
73/08/05
73/i)9/16
73/10/1H
73/11/11
73/12/16
74/01/05
74/0 1/20
7^/02/05
74/02/20
00630 00625
TIME DEPTH NO2&N03 TOT KJEL
OF N-TOTAL N
DAY FEET
10
09
10
11
14
08
K
10
09
15
10
14
14
13
45
SO
50
15
50
30
15
15
?5
OP
05
00
00
<*5
MG/L
0.310
J.230
0.330
0.273
0.370
U.399
0.410
0.336
0.273
0.276
0.250
i) . 340
0.312
0.300
MG/L
1.680
1.680
1.300
0.200
0.320
0.4QO
0.920
0.100K
0.150
0.100
0.100
0.100K
0.300
0.100
00610 00671 00665
NH3-N PHOS-OIS PHOS-TOT
TOTAL ORTHO
MG/L
0.069
0.140
0.048
0.027
0.080
0.037
0.043
0.040
C.033
0.051
J.032
0.032
0.030
0.030
MG/L P
0.008
0.015
0.005K
0.006
0.005K
0.005K
0.005K
0.005K
0.026
0.012
0.012
0.008
0.010
0.007
Mo/L P
0.015
0.060
0.015
0.020
0.010
0.015
0.010
0.015
0.060
0.017
0.040
0.010
O.Olo
0.015
K VALUE KNOWN TO bt
LESS THAN INDICATED
-------
STORE! RETRIEVAL DATE 76/07/22
0107G1 LS0107G1
32 48 00.0 085 47 JO.O 4
SANDY CHEEK (N AND S FORKS)
01 MAP TALLAPOOSA C
T/MAKTIN RESVR 033491
BtflDG ON ST KT <*9 1.5 MI SW OF DADEV1LLE
11EPALES 2111204
0000 FEET DEPTH CLASS 00
DATE
FROM
TO
73/03/04
73/04/08
73/05/16
73/06/09
73/07/14
73/08/0**
73/09/16
73/1U/18
73/11/11
73/12/15
74/01/05
7W01/20
74/02/05
74/02/20
00630 00625
TIME DEPTH N02NN03 TOT KJEL
OK N-TOTAL N
DAY FEET
10
09
10
10
14
14
14
09
09
11
10
13
14
13
30
30
30
40
30
30
05
45
15
15
00
40
30
30
MG/L
0
0
0
0
u
C
0
0
0
0
0
0
0
0
.198
.087
.198
.250
.220
.200
.189
.180
.100
.208
.160
.232
.224
.184
MG/L
1.
3.
0.
0.
2.
0.
0.
0.
0.
0.
0.
0.
0.
0.
760
300
900
3?0
700
240
330
100K
275
100
200
200
100
650
00610 00671 00665
NH3-N PHOS-DIS PHOS-TOT
TOTAL ORTHO
MG/L
0.
0.
0.
0.
0.
0.
0.
C.
0.
0.
0.
0.
0.
0.
056
198
017
042
320
014
027
026
029
028
028
044
020
040
MG/L
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
o.
C.
p
009
020
005K
Oil
008
005K
024
022
016
005K
012
008
010
010
MG/L P
0.020
0.065
0.015
0.055
0.030
0.025
0.035
0.050
0.055
0.020
0.040
0.015
0.02b
0.025
K VALUE KNOw'N TO BE
LESS THAN INDICATED
-------
STORET RETRIEVAL DATE 76/07/22
OlOfi-il LS0107H1
32 50 00.0 086 02 00.0 4
OAK4CHOY CREEK
01 MAP COOSA CO
T/MARTIN LAKE 033592
BROG ON RD 6 MI NE OF EQUALITY
11F.PALES 2111204
0000 FEET DEPTH CLASS 00
DATE
FROM
TO
73/03/03
73/03/25
73/04/28
73/05/24
73/06/23
73/07/14
73/09/15
73/10/09
73/10/15
73/12/18
74/01/05
74/01/09
74/01/19
74/02/02
00630 00625
TIME DEPTH N02^N03 TOT KJEL
OF N-TOTAL N
DAY FEET
15
08
13
13
13
10
09
08
10
09
11
10
09
08
30
45
50
10
35
30
10
30
15
40
10
00
50
40
M13/L
0
0
0
0
0
0
0
0
0
0
c
0
0
0
.036
.064
.048
.091
.080
.090
.086
.076
.031
.014
.192
.064
.068
.060
MG/L
1.
1.
0.
1.
0.
0.
0.
1.
0.
0.
0.
0.
0.
0.
400
800
320
200
210
140
460
440
600
100
200
600
100K
100K
00610 00671 00665
NH3-N PHOS-DIS PHOS-TOT
TOTAL ORTHO
MG/L
0
0
0
0
0
0
c
0
0
0
0
0
0
0
.072
.450
.021
.054
.013
.015
.025
.315
.025
.016
.044
.016
.015
.020
MG/L P
0
0
0
0
0
0
0
0
0
0
0
c
0
0
.013
.030
.014
.029
.014
.012
.019
.014
.019
.016
.016
.016
.015
.015
MG/L r>
0.015
0.115
0.030
0.115
0.030
0.030
0.050
0.035
0.040
0.040
0.035
0.025
0.020
K VALUE KNOWN TO OE
LESS THAN INDICATED
-------
STORET RETRIEVAL DATE 76/07/22
0107AA PD0107AA P001000
33 09 00.0 065 30 00.0 4
WAQLEl'
01 KANDALL CO HWY
T/MARTIN LAKE 033491
MUTTON CREEK/TALLAPOOSA RIVER
11EPALES 2141204
0000 FEET DEPTH CLASS 00
DATE
FROM
TO
73/07/30
73/08/27
73/09/25
73/10/29
73/11/26
73/12/26
74/01/28
74/02/25
74/04/05
74/04/30
74/35/26
74/06/26
00630
TIME DEPTH N02&.N03
OF N-TOTAL
DAY FEET
08
08
08
08
08
09
08
08
08
08
08
08
30
00
30
no
00
00
30
15
30
30
30
30
MG/L
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
080
050
025
420
720
120
640
440
280
040
132
00625
TOT KJEL
N
MG/L
6.500
8.20C
6.300
6.300
4.400
5.700
6.000
5.800
12.000
11.000
14.000
11.000
00610 00671 00665
NH3-N PHOS-DIS PHOS-TOT
TOTAL ORTHO
MG/L
0.087
0.019
0.600
0.048
0.300
0.120
C.094
0.570
1.900
1.300
0.910
0.060
MG/L P
1.600
4.120
3.200
5.000
3.990
4.600
4.200
4.300
4.200
5.000
5.200
4.800
50051 50053
FLOrt CONDUIT
RATE FLOd-MGD
MG/L P INST
4.530
5.000
3.600
5.500
4.600
5.200
6.703
5.000
6.200
6.700
7.500
6.400
0
0
0
0
u
0
0
0
0
0
0
0
MGU MONTHLY
.040
.040
.039
.040
.040
.040
.040
.040
.040
.340
.OM
.041
0.040
0.040
0.040
0.036
0.040
0.040
0.040
0.040
0.040
0.200
0.041
0.040
-------
STORE! RETRIEVAL DATE 76/07/32
0107EA TF0107EA P001500
32 53 50.0 066 00 00.0 4
SPRING HILL (ALEXANDER CITY)
01 TALLAPOOSA CO HW
T/MARTIN LAKE 033592
ELKAMATCHEE RIVER
11EPALES 2141204
0000 FEET DEPTH CLASS 00
00630 00625 00610 00671 00665 50051 50053
DATE TIME DEPTH N02&N03 TOT KJEL NH3-N PHOS-DIS PHOS-TOT FLOW CONDUIT
FROM
TO
73/04/30
CP(T>-
73/04/30
73/05/31
CP(T)-
73/05/31
73/06/29
CP(T>-
73/06/29
73/07/31
CP(T)-
73/07/31
73/08/31
CP< T>-
73/08/31
73/10/01
CPU1-
73/10/01
73/10/31
CP-
73/10/31
73/11/29
CP-
73/11/29
73/12/31
CP(T)-
73/12/31
74/01/31
CPU>-
74/01/31
74/02/28
CP(T>-
74/02/28
74/03/28
CP(T)-
74/03/28
OF
DAY FEET
07
14
08
15
07
15
07
14
07
14
07
14
07
14
07
14
07
14
U7
14
C7
14
07
14
30
30
00
00
00
00
00
00
00
00
00
00
30
30
00
00
00
00
00
00
00
00
00
00
N-TOTAL
MG/L
0
0
5
0
0
0
0
0
0
0
0
0
.220
.240
.185
.150
.990
.760
.990
.580
.420
.040
.280
.200
N
MG/L
6
5
8
9
8
14
15
4
10
3
3
3
.400
.400
.125
.700
.800
.000
.500
.300
.000
.000
.200
.600
TOTAL
MG/L
1.790
0.840
3.100
2.600
4.800
5.400
1.050
1.200
0.150
1.100
0.910
ORTHO
MG/L P
0.840
0.630
1.470
0.905
2.060
0.140
3.800
1.000
0.810
0.440
0.670
0.410
RATE FLOW-MOD
MG/L P INST MOD MONTHLY
2.000
2.300
3.300
2.880
3.550
4.000
5.900
1.650
1.550
1.200
1.600
1.150
0.268
0.576
0.435
0.576
0.413
0.392
0.410
0.382
0.415
0.367
0.473
0.387
0.298
0.732
0.460
0.504
0.532
0.357
0.396
0.358
0.372
0.392
0.641
0.355
-------
STORET RETRIEVAL DATE 76/07/22
0107E6 PU0107EB P001000*
32 53 40.0 085 59 30.0 4
SUGAR CREEK (ALEXANDER CITY)
01 TALLAPOOSA CU HW
T/MARTIN LAKE 033491
SUGAR CREEK/ELKAHATCHEE RIVER
11EPALES 2141204
0000 FEET DEPTH CLASS 00
00630 00625 00610 00671 00665 50051 50053
DATE TIME DEPTH N02^N03 TOT KJEL NH3-N PHOS-DIS PHOS-TOT FLOW CONDUIT
FROM
TO
73/04/30
CPIT1-
73/04/30
73/05/31
CP(T>-
73/05/31
73/06/29
CP(T)-
73/06/29
73/07/31
CP(T>-
73/07/31
73/08/31
CPITl-
73/08/31
73/10/01
CP(T)-
73/10/01
73/10/31
CP(T)-
73/10/31
73/11/29
CPiri-
73/11/29
73/12/31
CPU>-
73/12/31
74/01/31
74/02/27
Ci-1 (T> -
74/02/27
74/03/27
CPIT1-
74/03/27
OF
DAY FEET
07
14
08
15
07
15
07
14
07
14
07
14
07
14
07
14
07
14
07
14
07
14
30
30
00
00
00
00
00
00
00
00
00
00
30
30
00
no
00
00
00
on
00
00
N-TOTAL
MG/L
0
0
0
0
0
0
0
0
0
0
0
0
.090
.100
.150
.200
.092
.130
.126
.100
.110
.320
.120
.080
N
MG/L
14.700
13.800
12.600
14.000
12.600
14.700
13.500
11.500
83.000
11.000
9.000
11.000
TOTAL ORTHO
MG/L MG/L P
3
2
3
1
2
0
1
1
0
0
1
.200
.300
.300
.200
.300
.165
.300
.050
.470
.050K
.000
5.580
6.500
6.600
5.400
4.800
0.100
5.300
5.400
4.100
5.400
4.600
5.000
RATE FLOw-MGD
MG/L P INST MOD MONTHLY
6.700
7.700
8.100
7.000
6.700
6.000
7.900
7.000
5.800
7.100
6.400
6.700
4.700
4.880
5.170
5.450
5.510
5.080
5.510
5.630
4.210
5.250
4.790
4.760
4.630
4.290
4.760
4.750
4.690
5.100
5.240
4.760
4.490
5.310
4.250
3.520
K VALUE KNOWN TO HE
LESS THAN INDICATED
-------
STORET RETRIEVAL DATE 76/07/23
0107GA AS0107GA P001749
32 57 50.0 585 56 00.0 4
DOB8S CKEEK (ALEXANDER CITY)
01 TALLAHOOSA CO Hi*
T/MAHTIN LAKE 033491
UObBS CREEK/SANDY CREEK
11EPALES 214120*
0000 FEET DEPTH CLASS 00
DATE
FROM
TO
73/04/30
CP-
73/04/30
73/05/31
cpm-
73/05/31
73/06/29
CPITI-
73/06/29
73/07/31
CP(TI-
73/07/31
73/08/31
CPU>-
73/08/31
73/10/01
CP-
73/10/01
73/10/31
CP(T>-
73/10/31
73/11/29
cpm-
73/11/29
73/12/04
73/12/31
CPUl-
73/12/31
74/01/31
CP(T)-
74/01/31
74/02/27
CP(T)-
74/02/27
74/03/27
CP(T)-
74/03/27
00630
TIME DEPTH N02(iN03
OF N-TOTAL
DAY FEET MG/L
07
14
OS
15
07
15
07
14
07
14
07
14
07
14
07
14
07
14
u7
14
U7
14
07
14
30
30
00
00
00
00
00
00
00
00
00
00
30
30
00
00
00
00
00
OP
00
oo
00
00
6.200
0.280
0.115
(i.720
5.200
9.200
16.0CO
0.400
3.500
4.500
6.600
11.800
00625
TOT KJEL
N
MG/L
i.
4.
5.
2.
1.
0.
1.
0.
10.
0.
0.
1.
1.
400
600
200
300
200
950
600
660
000
880
600
OOOK
600
00610 00671 00665 SOObl 50053
NH3-N PHOS-DIS PHOS-TOT FLOW CONDUIT
TOTAL ORTHO RATE FLOW-MOD
MG/L MG/L P MG/L P INST MOD MONTHLY
0.780
1.580
0.720
0.500
0.055
0.230
0.071
2.300
0.058
0.040K
0.076
0.091
2.750
0.602
2.700
3.900
6.800
3.300
5.700
5.400
7.700
0.840
1.400
1.700
3.100
2.750
0.900
3.200
4.400
7.500
3.450
6.600
6.000
8.400
1.000
1.550
2.000
3.600
0
0
0
0
0
0
0
0
0
0
0
0
.620
.742
.632
.607
.516
.716
.491
.239
.641
.716
.566
.646
0.731
0.752
0.674
0.621
0.535
0.513
0.492
0.486
0.470
0.788
0.824
0.612
K VALUE KNOWN TO BE
LESS THAN INDICATED
-------
STORET RETRIEVAL DATE 76/07/28
0107GB AS0107GB P002300
32 57 50.0 087 57 30.0 4
CHRISTIAN CREEK (ALEXANDER CITY)
01 TALLAPOOSA CO HW
T/MARTIN LAKE 033992
SANDY CREEK
11EPALES 2141204
0000 FEET DEPTH CLASS 00
DATE
FROM
TO
73/04/30
CP ( T > -
73/04/30
73/05/31
CP(T>-
73/05/31
73/06/29
CP-
73/06/29
73/07/31
CP-
73/07/31
73/08/31
CP < T > -
73/OB/31
73/10/01
CP-
73/10/01
73/13/31
CP(T)-
73/10/31
73/11/29
CP(T)-
73/11/29
73/12/31
CP(T>-
73/12/31
74/01/30
CPITl-
74/01/30
74/02/27
CP(T)-
74/02/27
74/03/27
CP(T)-
74/03/27
00630 00625
TIME DEPTH N02&N03 TOT KJEL
OF N-TOTAL N
DAY FEET MG/L MG/L
06
13
08
15
07
15
07
14
07
14
07
14
07
14
07
14
07
14
07
14
07
14
07
14
30
30
00
00
00
00
00
00
00
00
00
00
30
30
00
00
00
00
00
00
00
00
00
00
3.700
1.400
1.200
7.400
0.650
1.000
1.980
4.800
4.300
5.200
3.600
1.
3.
1.
0.
1.
1.
4.
1.
0.
0.
1.
2.
800
600
900
800
225
100
250
150
910
800
OOOK
000
00610 00671 00665 50051 50053
NH3-N PHOS-DIS PHOS-TOT FLOW CONDUIT
TOTAL ORTHO RATE FLOw-MGD
MG/L MG/L P MG/L P INST MGD MONTHLY
0.400
0.920
1.050
0.040
0.290
0.570
0.290
0.046
0.087
0.050K
0.145
0.680
0.600
1.200
2.500
3.240
2.100
2.900
1.320
0.675
0.740
0.720
1.450
2.700
1.350
1.700
3.100
3.450
2.500
3.500
1.580
1.000
0.920
1.150
1.750
0
0
0
0
0
0
0
0
1
1
0
0
.730
.888
.835
.630
.557
.560
.492
.646
.030
.000
.520
.712
0.810
0.970
0.838
0.553
0.605
0.505
0.575
0.626
0.726
1.730
0.587
0.639
K VALUE KNOWN TO BE
LESS THAN INDICATED
-------
STORE! RETRIEVAL DATE 7h/07/22
U107GC PU0107GC P000900
32 48 00.0 085 3V 00.0 4
CAMP MILL
01 TALLAPOOSA CU HW
T/MAKTIN LAKE 033491
SANDY CREEK
11EPALES 21412U4
0000 FEET DEPTH CLASS 00
JATE
FROM
TO
73/09/28
73/11/05
74/01/02
74/01/28
74/02/28
74/03/28
74/07/01
74/07/29
74/OR/29
74/09/30
TIME: DEPTH
OF
DAY FEET
14 30
13 00
09 45
09 00
08 00
iO 00
15 00
16 15
13 40
12 30
00630
N02&N03
iJ-TOTAL
MG/L
0.250
0.110
0.480
0.040
0.320
0.200
0.040
O.OrtO
7.700
4.000
00625
TOT KJEL
N
MG/L
12.000
15.000
10.500
14.000
6.800
12.500
8.800
12.000
8.800
10.000
00610
NH3-N
TOTAL
MG/L
2.400
1.200
1.320
2.620
1.000
2.300
O.C50K
0.710
0.820
1.150
00671
PHOS-DIS
ORTHO
MG/L P
12.000
10.200
4.900
4.900
3.500
5.400
7.000
7.900
6.900
5.100
00665
PHOS-TOT
MG/L P
15.000
14.000
6.600
6.200
4.500
7.100
8.000
9.900
6.900
5.750
50051
FLOW
RATE
INSF MGU
0.085
0.087
50053
CONDUIT
FLOW-MGD
MONTHLY
0.080
0.085
0.087
K VALUE KNOWN TO BE
LESS THAN INDICATED
-------
STORET RETRIEVAL DATE 76/07/22
0107(3D PU0107GD P001508
32 47 45.0 085 46 15.0 4
DADEVILLE
01 TALLAPOOSA CO. HW
T/MARTIN LAKE 0334^1
SANDY CREEK
11EPALES 2141204
0000 FEET DEPTH CLASS 00
DATE
FROM
TO
73/10/23
74/03/06
74/04/10
TIMF DEPTH
OF
DAr
08
oa
08
FEET
00
00
00
00630
N02&N03
N-TOTAL
MG/L
0.2JO
O.POO
0.080
00625
TOT KJEL
N
MG/L
12.500
9.300
6.400
00610
NH3-N
TOTAL
MG/L
0.880
3.000
1.250
00671
PHOS-OIS
ORTHO
MG/L P
12.000
10.500
8.700
00665
PHOS-TOT
50051
FLOW
RATE
MG/L
K.
10.
10.
P
500
500
500
1NST
0
0
0
MGD
.004
.200
.200
50053
CONuUIT
FLOW-MGD
MONTHLY
0.004
0.200
0.200
-------
STORET RETRIEVAL DATE 76/07/22
0107JA AS0107JA P003000«
32 51 30.0 085 50 JO.O 4
COLEY CREEK (ALEXANDER CITY)
01 TALLAPOOSA CO HW
T/MARTIN LAKE 033491
COLEY CREEK
11EPALES 214120'.
0000 FEET DEPTH CLASS 00
00630 00625 00610 00671 00665 50051 50053
DATE TIME DEPTH N02&N03 TOT KJEL NH3-N PHOS-DIS PHOS-TOT FLOW CONDUIT
FROM
TO
73/04/30
C> ( T ) -
73/04/30
73/05/31
CP-
73/05/31
73/06/29
CP(T>-
73/06/29
73/07/31
CP(T>-
73/07/31
73/08/31
CP(T>-
73/Od/31
73/10/01
CP-
73/10/01
73/10/31
CP-
73/10/31
73/11/29
CP(T>-
73/11/29
73/12/31
CP(T)-
73/12/31
74/01/31
CP(T)-
74/01/31
74/02/28
CPIT1-
74/02/26
74/03/28
CP(T)-
74/03/28
OF
DAY FEET
07
14
08
15
07
15
07
14
07
14
07
14
07
14
07
14
07
14
07
14
07
14
07
14
30
30
00
00
00
00
00
00
00
00
00
no
30
30
00
00
00
on
00
00
00
00
00
00
N-TOTAL
MG/L
3
0
0
0
0
1
2
0
2
0
1
0
.800
.440
.138
.560
.115
.260
.520
.460
.310
.0*0
.000
.040
N
MG/L
2.700
7.600
14.000
10.500
10.000
10.200
15.500
11.000
7.900
5.800
4.000
9.400
TOTAL
MG/L
0.150
1.700
2.800
3.300
4.300
2.300
2.600
1.890
0.071
0.110
1.250
ORTHO
MG/L P
2.400
3.000
5.300
5.500
6.700
4.700
8.900
3.600
2.100
2.520
3.700
3.800
RATE FLOW-MGD
MG/L P INST MGD MONTHLY
2.700
3.600
7.350
6.400
9.500
4.900
11.000
4.500
3.150
3.300
4.100
5.300
1
1
1
0
0
0
0
0
0
1
0
0
.040
.210
.030
.688
.581
.851
.526
.702
.999
.250
.838
.986
0.908
1.200
0.958
0.676
0.691
0.526
0.389
0.656
0.709
0.985
0.835
0.792
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APPENDIX E
PARAMETRIC RANKINGS OF LAKES
SAMPLED BY NES IN 1974
STATE OF ALABAMA
-------
LAKE DATA TO BE USED IN RANKINGS
LAKE
CODE LAKE NAME
0101 8ANKHEAD LAKE
0103 GANTT RESERVOlw
0104 GUNTERSVILLE RESERVOIR
0105 HOLT LOCK AND 0AM
0106 LAY LAKE
0107 MARTIN LAKE
010* MITCHELL LAKE
0109 PICKWICK LAKE
0112 WEISS RESERVOIR
0114 WILSON LAKE
0115 LAKE
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
CriLOWA
4.017
2.144
8.567
2.183
7.056
6.407
6.211
2.450
11.261
7.400
12.711
Ib-
MlN 00
14.900
14.000
12.200
13.600
13.000
15.000
12.400
11.900
14.900
10.200
15.000
MEDIAN
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 OF LAKES WITH HIGHER VALUES (NUMBER OF LAKES WITH HIGHER
LAKE
CODE LAKE NAME
0101 8ANKHEAD LAKE
0103 GANTT RESERVOIR
0104 GUNTERSVILLE RESERVOIR
0105 HOLT LOCK AND 0AM
0106 LAY LAKE
0107 MARTIN LAKE
0108 MITCHELL LAKE
0109 PICKWICK LAKE
0112 WEISS RESERVOIR
0114 WILSON LAKE
0115 LAKE PURDY
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 (
4C (
70 (
10 (
100 (
20 (
50 (
0 (
80 <
90 (
6)
3)
4)
7)
1)
10)
2)
5)
0)
8)
9)
MEAN
CHLOfA
70 (
100 (
20 (
90 (
40 (
50 (
60 (
80 (
10 (
30 (
0 (
7)
10)
2)
9)
<*)
5)
6)
d)
1)
3)
0)
15-
MIN i
25 (
40 (
80 (
50 (
60 (
5 (
70 (
90 (
25 (
100 (
5 (
lO
2)
4)
8)
5)
6)
0)
7)
9)
2)
10)
0)
MEDIAN
DISS Ok TrtO P
80 (
70 (
55 (
90 (
20 (
100 (
35 (
0 (
10 (
35 (
55 (
8)
7)
5)
9)
2)
10)
3)
0)
1)
3)
5)
INDEX
NO
320
375
2d5
390
190
450
295
260
125
315
295
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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 LA*E 320
5 0114 WILSON LAKE 315
6 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
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