U.S. ENVIRONMENTAL PROTECTION AGENCY
NATIONAL EUTROPHICATION SURVEY
WORKING PAPER SERIES
REPORT
ON
BURTON LAKE
RABUN COUNTY
GEORGIA
EPA REGION IV
WORKING PAPER No, 285
PACIFIC NORTHWEST ENVIRONMENTAL RESEARCH LABORATORY
An Associate Laboratory of the
NATIONAL ENVIRONMENTAL RESEARCH CENTER - CORVALLIS, OREGON
and
NATIONAL ENVIRONMENTAL RESEARCH CENTER - LAS VEGAS, NEVADA
RGPO 697.032
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REPORT
ON
BURTON LAKE
RABUN COUNTY
GEORGIA
EPA REGION IV
WORKING PAPER No, 285
WITH THE COOPERATION OF THE
GEORGIA DEPARTMENT OF NATURAL RESOURCES
AND THE
GEORGIA NATIONAL GUARD
JUNE, 1975
794
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CONTENTS
Page
Foreword i i
List of Georgia Study Lakes iv
Lake and Drainage Area Map v
Sections
I. Conclusions 1
II. Lake and Drainage Basin Characteristics 4
III. Lake Water Quality Summary 5
IV. Nutrient Loadings 10
V. Literature Reviewed 15
VI. Appendices 16
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1i
FOREWORD
The National Eutrophication Survey was initiated in 1972 in
response to an Administration commitment to investigate the nation-
wide threat of accelerated eutrophication to fresh water lakes and
reservoirs.
OBJECTIVES
The Survey was designed to develop, in conjunction with state
environmental agencies, information on nutrient sources, concentrations,
and impact on selected freshwater lakes as a basis for formulating
comprehensive and coordinated national, regional, and state management
practices relating to point-source discharge reduction and non-point
source pollution abatement in lake watersheds.
ANALYTIC APPROACH
The mathematical and statistical procedures selected for the
Survey's eutrophication analysis are based on related concepts that:
na. A generalized representation or model relating
sources, concentrations, and impacts can be constructed.
b. By applying measurements of relevant parameters
associated with lake degradation, the generalized model
can be transformed into an operational representation of
a lake, its drainage basin, and related nutrients.
c. With such a transformation, an assessment of the
potential for eutrophication control can be made.
LAKE ANALYSIS
In this report, the first stage of evaluation of lake and water-
shed data collected from the study lake and its drainage basin is
documented. The report is formatted to provide state environmental
agencies with specific information for basin planning [§303(e)], water
quality criteria/standards review [§303(c)], clean lakes [§314(a,b)],
and water quality monitoring [§106 and §305(b)] activities mandated
by the Federal Water Pollution Control Act Amendments of 1972.
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Beyond the single lake analysis, broader based correlations
between nutrient concentrations (and loading) and trophic condi-
tion are being made to advance the rationale and data base for
refinement of nutrient water quality criteria for the Nation's
fresh water lakes. Likewise, multivarlate evaluations for the
relationships between land use, nutrient export, and trophic
condition, by lake class or use, are being developed to assist
1n the formulation of planning guidelines and policies by EPA
and to augment plans implementation by the states.
ACKNOWLEDGMENT
The staff of the National Eutrophication Survey (Office of
Research 4 Development, U. S. Environmental Protection Agency)
expresses sincere appreciation to the Georgia Department of
Natural Resources for professional involvement and to the
Georgia National Guard for conducting the tributary sampling
phase of the Survey.
Joe D. Tanner, Commissioner of the Department of Natural
Resources; J. Leonard Ledbetter, Director of the Environmental
Protection Division; Ralph S. Howard, Jr., Environmental Affairs
Coordinator; Gene B. Welsh, Chief of the Water Protection Branch;
Edward T. Hall, Jr., Unit Coordinator; and Broughton A. Caldwell,
R. Marshall Gaddls, William D. Kennedy, and Kenneth W. Martin,
Environmental Specialists, provided invaluable lake documentation
and counsel during the Survey, reviewed the preliminary lake reports,
and provided critiques most'useful in the preparation of this
Working Paper series.
Major General Joel B. Paris, III, then the Adjutant General of
Georgia, and Project Officer Lt. Colonel John R. Ranier, who directed
the volunteer efforts of the Georgia National Guardsmen, are also
gratefully acknowledged for their assistance to the Survey.
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1v
LAKE NAME
Allatoona
Blackshear
Blue Ridge
Burton
Chatuge
Clark Hill
Harding
Hartwel1
High Falls
Jackson
Nottely
Semi nole
Sidney Lanier
Sinclair
Walter F. George
NATIONAL EUTROPHICATION SURVEY
STUDY LAKES
STATE OF GEORGIA
COUNTY
Bartow, Cherokee, Cobb
Crisp, Dooly, Lee, Sumpter,
Worth
Fannln
Rabun
Towns, GA; Clay, NC
Columbia, Elbert, Lincoln,
McDuffie, Wilks, GA;
Abbeville, McCormick, SC
Harris, GA; Chambers, Lee, AL
Franklin, Hart, Stephens, GA;
Anderson, Oconee, Pickens, SC
Butts, Lamar, Monroe
Butts, Jasper, Newton
Union
Decatur, Seminole, GA;
Jackson, FL
Dawson, Forsyth, Gwinnett,
Hall, Lumpkin
Baldwin, Hancock, Putnam
Clay, Quitman, Stewart, GA;
Barbour, Henry, Russell, AL
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LAKE
Nacoochee Lake I
BURTON LAKE
Tributary Sampling Site
X Lake Sampling Site
~3 Drainage Area Boundary
0 24 6 8 i/m
Km,
2 3 4 5 Ml .
Scale
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BURTON LAKE*
STORE! NO. 1318
I. CONCLUSIONS
A. Trophic Condition:
Survey data indicate that Burton Lake is mesotrophic. It
ranked second in overall quality when all 14 Georgia lakes
sampled in 1973 were compared using a combination of six param-
eters**. None of the lakes had less median total phosphorus,
dissolved phosphorus, and inorganic nitrogen; one lake had less
mean chlorophyll a_; and none had greater mean Secchi disc trans-
parency.
Survey limnologists did not observe algal concentrations or
macrophytes. However, hypolimnetic dissolved oxygen was depressed
to less than 1.0 mg/1 at all stations in September.
B. Rate-Limiting Nutrient:
The algal assay results indicate that Burton Lake was
phosphorus limited at the time the sample was collected (06/28/73).
The lake data indicate phosphorus limitation in June and September,
1973, also; i.e., the mean inorganic nitrogen to orthophosphorus
ratios were 18 to 1 or greater.
* Table of metric conversions—Appendix A.
** See Appendix B.
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C. Nutrient Controllability:
1. Point sources—No municipal wastewater treatment plants
discharged to Burton Lake during the sampling year; however, the
Burton Lake State Fish Hatchery discharged to Moccasin Creek
(Anonymous, 1972). Nutrient contributions from this source were
not measured but probably were not significant (see below).
Septic tanks serving permanent and seasonal dwellings on the
lakeshore were estimated to have contributed 4.8% of the total
phosphorus load to the lake, but a shoreline survey would be
necessary to determine the actual contribution of these sources.
The present loading rate of 0.40 g/m2/yr is less than the
rate proposed by Vollenweider (Vollenweider and Dillon, 1974) as
"permissible"; i.e., an oligotrophic rate (see page 14). The
existing loading rate should result in continuance of the high
quality of Burton Lake.
2. Non-point sources—The phosphorus load from non-point
sources, including precipitation amounted to 95.2% of the total
reaching Burton Lake during the sampling year. The Tallulah
River contributed 46.9%, Timpson Creek supplied 15.7%, Moccasin
Creek contributed 7.0%, and the remaining three tributaries
supplied a total of 9.5%. The contributions from ungaged tribu-
taries were estimated to have been 11.7% of the total load.
-------
Moccasin Creek was sampled just downstream from the overflows
of the fish-rearing raceways of the Burton Lake State Fish Hatchery
(Caldwell, 1975). Therefore, the phosphorus load measured in the
creek included that resulting from the hatchery operation. However,
the calculated phosphorus export rate of Moccasin Creek was only
15 kg/km2/yr, and this is comparable to the mean export rate of 13
kg/km2/yr of the other five sampled tributaries (see page 12). On
this basis, it is believed that the hatchery phosphorus contribution
was not significant during the Survey sampling year.
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II. LAKE AND DRAINAGE BASIN CHARACTERISTICS
A. Lake Morphometry :
1. Surface area: 11.23 kilometers2.
2. Mean depth: 11.9 meters.
3. Maximum depth: >30.5 meters.
4. Volume: 133.637 x 106 m3.
5. Mean hydraulic retention time: 161 days.
B. Tributary and Outlet:
(See Appendix C for flow data)
1. Tributaries -
Drainage Mean flow
Name area (km2) (m3/sec)
Tallulah River 147.6 5.0
Wildcat Creek 16.1 0.6
Moccasin Creek 20.7 0.7
Dicks Creek 17.9 0.6
Popcorn Creek 15.0 0.5
Timpson Creek . 27.7 0.9
Minor tributaries &
immediate drainage - 41.7 1.3
Totals 286.7 9.6
2. Outlet -
Tallulah River 297.9** 9.6
C. Precipitation***:
1. Year of sampling: 229.8 centimeters.
2. Mean annual: 176.2 centimeters.
t Martin and Hanson, 1966.
* For limits of accuracy, see Working Paper No. 175, "...Survey Methods,
1973-1976".
** Total area adjusted to equal sum of the subdrainage areas plus the area
of the lake.
*** See Working Paper No. 175.
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III. LAKE WATER QUALITY SUMMARY
Burton Lake was sampled three 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
three stations on the lake and from a number of depths at each station
(see map, page i). During each visit, a single depth-integrated
(4.6 m to surface) sample was composited from the three stations for
phytoplankton identification and enumeration; and during the first
visit, a single 18.9-liter depth-integrated sample was composited for
algal assays. Also each time, a depth-integrated sample was collected
from each of the stations for chlorophyll a_ analysis. The maximum
depths sampled were 30.5 meters at station 1, 14.3 meters at station 2,
and 15.2 meters at station 3.
The lake sampling results are presented in full in Appendix D and
are summarized in the following table.
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A. SUMMARY OF PHYSICAL AND CHEMICAC CHARACTERISTICS FOR BURTON LAKE
STORET CODE 1318
PARAMETER
TEMP (C)
OISS OXY (MG/L)
CNDCTVY (MCROMO)
PH (STAND UNITS)
TOT ALK (MG/L)
TOT P (MG/L)
ORTHO P (M.G/L)
N02*N03 (MC,/L>
AMMONIA (MG/L)
KJEL N (MG/L)
INORG N (MG/L)
TOTAL N (MG/L)
CHLRPYL A (Ufi/L)
SECCHI (METERS)
1ST SAMPLING ( 6/38/73)
3 SITES
2ND SAMPLING ( 9/18/73)
3 SITES
3RD SAMPLING (11/10/73)
3 SITES
RANGE
12.8
2.1
SO.
6.3
10.
0.006
0.002
0.040
0.060
0.200
0.100
0.240
2.0
?.5
- 27.0
- 10.1
50.
7.1
13.
- 0.014
- 0.004
- 0.080
- 0.170
- 0.600
- 0.230
- 0.670
5.7
3.2
MEAN
21.3
7.2
50.
6.7
10.
0.008
0.002
0.056
0.076
0.?94
0.132
0.351
3.5
2.R
MEDIAN ;
21.6
7.7
50.
6.5
10.
0.009
0.002
0.050
0.060
0.300
0.120
0.340
2.8
2.7
. RANGE
15.2
0.1
14.
5.3
10.
0.004
0.004
0.020
0.040
0.200
0.060
0.230
2.4
2.8
- 24.5
8.0
24.
7.1
13.
- 0.024
- 0.009
- 0.100
- 0.200
- 0.800
- 0.240
- 0.820
3.7
3.0
MEAN
21.0
3.9
17.
5.9
10.
0.009
0.006
0.040
0.069
0.373
0.109
0.413
3.0
2.9
MEDIAN
21.7
3.2
16.
5.8
10.
0.008
0.006
0.030
0.040
0.400
0.080
0.430
3.0
2.8
RANGE
14.7
7.2
17.
6.3
10.
0.005
0.020
0.040
0.200
0.060
0.220
1.3.
3.7
- 15.9
8.4
20.
6.5
11.
- 0.010
- 0.030
- 0.060
- 0.300
- 0.090
- 0.330
2.1
- 5.5
MEAN
15.3
7.9
18.
6.4
10.
0.007
0.022
0.048
0.208
0.069
0.229
1.7
4.7
MEDIAN
15.4
7.9
18.
6.4
10.
0.006
0.020
0.050
0.200
0.070
0.220
1.6
5.0
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B. Biological characteristics:
1. Phytoplankton -
Sampling
Date
06/28/73
09/18/73
11/10/73
Dominant
Genera
1.
2.
3.
4.
5.
1.
2.
3.
4.
5.
1.
2.
3.
4.
5.
Flagellates
Peri dim' urn
Mallomonas
Oscillatoria
Dinobryon
Other genera
Total
Gloeocystis
Kirchneriella
Cyclotella
Merismopedia
Peri dini urn
Other genera
Total
Lyngbya
Asterionella
Melosira
Ankistrodesmus
Microcystis
Other genera
Total
Algal units
per ml
103
52
30
30
15
29
259
139
123
92
92
31
139
616
398
121
86
69
35
119
828
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8
2. Chlorophyll a. -
Sampling
Date
06/28/73
09/18/73
11/10/73
Station
Number
01
02
03
01
02
03
01
02
03
Chlorophyll a_
(ug/1)
2.0
5.7
2.8
2.4
3.7
3.0
1.6
1.3
2.1
C. Limiting Nutrient Study:
1. Autoclaved, filtered, and nutrient spiked -
Spike (mg/1)
Control
0
0
0
0
0
.010
.020
.050
.025
.050
P
P
P
P +
P +
0.
1.
5
0
N
N
1.0 N
Ortho P
Cone, (mg/1)
0.008
0.018
0.028
0.058
0.033
0.058
0.008
2.
Filtered and nutrient spiked -
Spike (mg/1)
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)
Inorganic N
Cone, (mg/1)
0.094
0.094
0.094
0.094
0.594
1.094
1.094
Inorganic N
Cone, (mg/1)
0.004
0.014
0.024
0.054
0.029
0.054
0.004
0,
0,
0,
0.
088
088
088
088
0.588
1.088
1.088
Maximum yield
(mg/1-dry wt.)
0.1
0.2
1.3
1.7
7.8
18.7
0.1
Maximum yield
(mg/1-dry wt.)
0.1
0.3
1.3
1.2
7.4
15.6
0.1
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3. Discussion -
The control yields of the assay alga, Selenastrum capri-
cornutum, indicate that the potential primary productivity
of Burton Lake was low at the time the assay sample was
collected (06/28/73). Increasing algal yields with increas-
ing concentrations of orthophosphorus indicate that Burton
Lake was limited by phosphorus at that time. Note that the
addition of only nitrogen did not result in an increased
yield.
The lake data obtained in June and September indicate
phosphorus limitation at those times also. On both occasions,
the mean inorganic nitrogen to orthophosphorus ratios were
18 to 1 or greater, and phosphorus limitation would be
expected.
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10
IV. NUTRIENT LOADINGS
(See Appendix E for data)
For the determination of nutrient loadings, the Georgia National
Guard collected monthly near-surface grab samples from each of the
tributary sites indicated on the map (page v)» except for the high
runoff months of January and February when two samples were collected.
Sampling was begun in March, 1973, and was completed 1n February, 1974.
Through an interagency agreement, stream flow estimates for the
year of sampling and a "normalized" or average year were provided by
the Georgia District Office of the U.S. Geological Survey for the
tributary sites nearest the lake.
In this report, nutrient loads for sampled tributaries were deter-
mined by using a modification of a U.S. Geological Survey computer
program for calculating stream loadings*. Nutrient loads shown are
those measured minus point-source loads, if any.
Nutrient loadings for unsampled "minor tributaries and immediate
drainage" ("ZZ" of U.S.G.S.) were estimated using the means of the
nutrient loads, in kg/km2/year, at stations B-l, D-l, E-l, and F-l
and multiplying the means by the ZZ area in km2.
See Working Paper No. 175.
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11
A. Waste Sources :
1. Known municipal - None
2. Known industrial -
Mean flow Receiving
Name Treatment (m3/day) Water
Burton Lake State unknown unknown Moccasin Creek
Fish Hatchery
t Anonymous,. 1972.
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12
B. Annual Total Phosphorus Loading - Average Year:
1. Inputs -
kg P/ % of
Source yjr total
a. Tributaries (non-point load) -
Tallulah River 2,090 46.9
Wildcat Creek 135 3.0
Moccasin Creek 310 7.0
Dicks Creek 165 3.7
Popcorn Creek 125 2.8
Timpson Creek 700 15.7
b. Minor tributaries & immediate
drainage (non-point load) - 520 11.7
c. Known municipal STP's - None
d. Septic tanks* - 215 4.8
e. Known industrial -
Burton Lake State Fish
Hatchery unknown
f. Direct precipitation** - 195 4.4
Total 4,455 100.0
2. Outputs -
Lake outlet - Tallulah River 2,005
3. Net annual P accumulation - 2,450 kg.
* Estimate based on 698 seasonal and 40 permanent lakeside residences;
see Working Paper No. 175.
** See Working Paper No. 175.
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13
C. Annual Total Nitrogen Loading - Average Year:
1. Inputs -
kg N/ % of
Source yr total
a. Tributaries (non-point load) -
Tallulah River 84,475 50.7
Wildcat Creek 6,835 4.1
Moccasin Creek 9,430 5.7
Dicks Creek 6,020 3.6
Popcorn Creek 5,215 3.1
Timpson Creek 16,595 10.0
b. Minor tributaries & immediate
drainage (non-point load) - 17,805 10.6
c. Known municipal STP's - None
d. Septic tanks* - 8,120 4.9
e. Known industrial -
Burton Lake State Fish
Hatchery unknown
f. Direct precipitation** - 12,125 7.3
Total 166,620 100.0
2. Outputs -
Lake outlet - Tallulah River 108,855 kg.
3. Net annual N accumulation - 57,765 kg.
* Estimate based on 698 seasonal and 40 permanent lakeside residences;
see Working Paper No. 175.
** See Working Paper No. 175.
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14
D. Mean Annual Non-point Nutrient Export by Subdralnage Area:
Tributary kg P/km2/yr kg N/km2/yr
Tallulah River 14 572
Wildcat Creek 8 425
Moccasin Creek 15 456
Dicks Creek 9 336
Popcorn Creek 8 348
Timpson Creek 25 599
E. Yearly Loading Rates:
In the following table, the existing phosphorus loading
rates are compared to those proposed by Vollenweider (Vollen-
weider and Dillon, 1974). Essentially, his "dangerous" rate
is the rate at which the receiving water would become eutrophic
or remain eutrophic; his "permissible" rate is that which would
result in the receiving water remaining ollgotrophic or becoming
oligotrophic if morphometry permitted. A mesotrophic rate would
be considered one between "dangerous" and "permissible".
Note that Vollenweider's model may not be applicable to
water bodies with short hydraulic retention times.
Total Phosphorus Total Nitrogen
Total Accumulated Total Accumulated
grams/m2/yr 0.40 0.22 14.8 5.1
Vpllenweider loading rates for phosphorus
(g/m2/yr) based on mean depth and mean
hydraulic retention time of Burton Lake:
"Dangerous" (eutrophic rate) 1.00
"Permissible" (oligotrophic rate) 0.50
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15
V. LITERATURE REVIEWED
Anonymous, 1972. Georgia municial and industrial wastewater treatment
facilities associated with reservoirs. GA Dept. of Nat. Resources,
Atlanta.
Anonymous, 1974. Water quality monitoring data for Georgia streams,
1973; volume 1. GA Dept. of Nat. Resources, Atlanta.
Caldwell, Broughton, 1975. Personal communication (Moccasin Creek
sampling station in relation to the Burton Lake State Fish Hatchery
discharges). GA Dept. of Nat. Resources, Atlanta.
Martin, R. 0. R., and Ronald L. Hanson, 1966. Reservoirs in the United
States. Water Supply Paper 1838, U.S. Geological Survey, Wash., D.C.
Vollenweider, R. A., and P. J. Dillon, 1974. The application of
the phosphorus loading concept to eutrophication research.
Natl. Res. Council of Canada Publ. No. 13690, Canada Centre
for Inland Waters, Burlington, Ontario.
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VII. APPENDICES
APPENDIX A
CONVERSION FACTORS
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CONVERSION FACTORS
Hectares x 2.471 = acres
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
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APPENDIX B
LAKE RANKINGS
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LAKES RANKED BY INDEX NOS.
RANK LAKE CODE LAKE NAME INDEX NO
1 1316 BLUE RIDGE LAKE 524
2 1318 BURTON LAKE 523
3 1303 CHATUGE LAKE 424
4 1311 NOTTELY RESERVOIR 393
5 1310 LAKE SIDNEY LANIER 385
6 1304 CLARK HILL RESERVOIR 309
7 1301 ALLATOONA RESERVOIR 286
8 1302 BLACKSHEAR LAKE 284
9 1313 SINCLAIR LAKE 254
10 1312 LAKE SEMINOLE 253
11 1319 HIGH FALLS LAKE 192
12 1314 LAKE EUFAULA 184
13 1309 JACKSON LAKE 116
14 1317 LAKE HARDING 77
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PERCENT OF LAKES WITH HIGHER VALUES (NUMBER OF LAKES WIT,. HIGHER VALUES)
LAKE
CODE LAKE NAME
1301 ALLATOONA RESERVOIR
1302 BLACKSHEAR LAKE
1303 CHATUGE LAKE
1304 CLARK HILL RESERVOIR
1309 JACKSON LAKE
1310 LAKE SIDNEY LANIER
1311 NOTTELY RESERVOIR
1312 LAKE SEMINOLE
1313 SINCLAIR LAKE
1314 LAKE EUFAULA
1316 BLUE RIDGE LAKE
1317 LAKE HARDING
1318 BURTON LAKE
1319 HIGH FALLS LAKE
MEDIAN
TOTAL P
62
38
85
54
8
69
77
31
46
15
92
0
100
23
( 8)
( 5)'
( 11)
( 7)
( 1)
( 9)
( 10)
( 4)
( 6)
( 2)
( 12)
( 0)
( 13)
( 3)
MEDIAN
INORG N
54
31
85
62
8
46
69
15
38
23
92
0
100
77
( 7)
( 4)
( 11)
( 8)
( 1)
( 6)
( 9)
( 2)
( 5)
( 3)
( 12)
( 0)
( 13)
( 10)
500-
MEAN SEC
46 (
0 (
92 (
62 <
15 (
77 (
69 (
38 (
54 (
31 (
85 (
8 (
100 (
23 <
6)
0)
12)
8)
2)
10)
9)
5)
7)
4)
11)
1)
13)
3)
MEAN
CHLORA
31 (
100 (
69 (
54 (
8 (
77 (
62 (
46 (
23 (
15 (
85 (
38 (
92 (
0 (
4)
13)
9)
7)
1)
10)
8)
6)
3)
2)
11)
5)
12)
0)
15-
MIN DO
31
100
31
31
69
31
31
92
31
77
85
31
31
31
( 0)
( 13)
( 0)
( 0)
( 9)
( 0)
< 0)
( 12)
( 0)
( 10)
< 11)
( 6)
( 0)
( 0)
MEDIAN
DISS P
62 (
15 (
62 (
46 (
8 (
85 (
85 (
31 (
62 (
23 (
85 (
0 (
100 (
38 (
7)
2)
7)
6)
1)
10)
10)
4)
7)
3)
10)
0)
13)
5)
INDEX
NO
286
284
424
309
116
385
. 393
253
254
184
524
77
523
192
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LAKE DATA TO BE USED IN RANKINGS
LAKE
CODE LAKE NAME
1301 ALLATOONA RESERVOIR
1302 BLACKSHEAR LAKE
1303 CHATUGE LAKE
1304 CLARK HILL RESERVOIR
1309 JACKSON LAKE
1310 LAKE SIDNEY LANIER
1311 NOTTELY RESERVOIR
1312 LAKE SEMINOLE
1313 SINCLAIR LAKE
131* LAKE EUFAULA
1316 BLUE RIDGE LAKE
1317 LAKE HARDING
1318 BURTON LAKE
1319 HIGH FALLS LAKE
MEDIAN
TOTAL P
0.020
0.035
0.014
0.024
0.094
0.016
0.015
0.040
0.028
0.048
0.010
0.114
0.007
0.047
MEDIAN
INOMG N
0.150
0.250
0.110
0.150
0.530
0.180
0.130
0.405
0.230
0.345
0.105
0.640
0.100
0.115
500-
MEAN SEC
443.167
468.091
382.778
439.250
461.385
396.417
405.667
456.133
440.667
457.667
394.889
467.538
363.889
459.444
MEAN
CHLORA
7.489
1.855
6.339 \
6.715
14.577
5.431
6.656
6.760
8.006
9.083
3.078
7.438
2.733
15.075
15-
MIN 00
14.900
11.700
14.900
\ 14.900
Vl4.800
\
14.900
\
14.90^0
11.800
14.900
14.400
13.000
14.900
14.900
14.900
MEDIAN
OISS P
0.005
0.014
0.005
0.007
0.027
0.004
0.004
0.010
0.005
0.011
0.004
0.045
0.003
0.009
-------
APPENDIX C
TRIBUTARY FLOW DATA
-------
TRIBUTARY FLOW INFORMATION FOR GEORGIA
12/2/75
LAKE CODE 1318 LAKE BURTON
TOTAL DRAINAGE AREA OF LAKE(SO KM)
SUB-DRAINAGE
TRIBUTARY AREA(SO KM)
JAN
FEB
397.8
MAR
APR
MAY
NORMALIZED FLOWS(CMS)
JUN JUL AUG
SEP
OCT
MOV
MAN
1318A1
1318A2
131881
1318C1
131801
1318E1
1318F1
1318ZZ
147.6
297.8
16.1
20.7
17.9
15.0
27.7
41.7
6.51
8.41
0.57
0.74
0.62
0.54
0.96
1.39
7.65 7.93 7.50 5.52 4.11 3.82 3.54 2.97 2.83 3.2* 4.3* 4.*9
7.16 5.95 9.06 10.96 9.40 7.76 9.03 10.42 12.94 12.12 11.41 .5*
0.71 0.79 0.76 0.59 0.54 0.51 0.42 0.4* t.37 .44 .51 .59
0.91 0.96 0.96 0.74 0.65 0.62 0.54 0.48 ».48 .51 .*2 .6*
0.76 0.85 0.82 0.65 0.57 0.57 0.45 0.42 0.40 .45 .57 .59
0.65 0.71 0.71 0.54 0.48 0.45 0.40 0.37 0.34 .37 .45 .50
1.19 1.30 1.27 0.99 0.88 0.85 0.71 0.65 0.62 .68 .85 .91
1.73 1.90 1.84 1.44 1.27 1.25 1.02 0.93 0.91 .99 .25 .32
SUMMARY
TOTAL DRAINAGE AREA OF LAKE
SUM OF SUB-DRAINAGE AREAS
297.8
286.7
TOTAL FLOW IN
TOTAL FLOW OUT
114.82
114.82
NOTE *•* LAKE AREA=4.3 SO MI, NOT INCLUDED IN SUM OF SUB-DRAINAGE AREAS
MEAN MONTHLY FLOWS AND DAILY FLOWS(CMS)
TRIBUTARY MONTH YEAR
1318A1
MEAN FLOW DAY
FLOW DAY
FLOW DAY
FLOW
1318A2
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
12.97
10.62
13.17
9.66
5.07
4.45
2.86
2.32
3.88
9.94
12.63
12.20
23.62
17.67
23.70
19.71
17.05
8.64
7.39
8.83
13.31
14.05
20.44
22.09
11
16
16
17
15
5
9
7
11
17
6
3
11
16
16
17
15
5
9
7
11
17
6
3
12.74
7.53
7.67
9.91
6.03
3.45
2.78
2.41
1.84
3.88
12.66
21.78
0.0
13.65
19.65
0.0
0.0
0.0
0.0
0.0
7.67
19.74
6.82
17.84
21
21
21
21
13.08
9.63
16.25
19.74
-------
TRIBUTARY FLOW INFORMATION FOR GEORGIA
13/2/75
LAKE CODE 1318
LAKE BURTON
MEAN MONTHLY FLOWS AND DAILY FLOWS
TRIBUTARY MONTH YEAR MEAN FLOW DAY
1318B1
1318C1
13)801
1318E1
3
4
5
6
7
8
9
10
11
12
1
2
3
4
5
6
7
a
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
I
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
1.42
1.16
1.44
1.05
0.54
0.48
0.31
0.34
0.48
1.02
.10
.13
.81
.50
.84
.36
0.71
0.62
0.40
0.31
0.54
.44
.42
.44
.56
.27
1.59
1.16
0.62
0.54
0.34
0.28
0.45
.22
.22
.22
.33
.08
.33
0.99
0.51
0.45
0.28
0.25
0.42
1.02
1.05
1.05
11
16
16
17
15
5
9
7
11
17
6
3
11
16
16
17
15
5
9
7
11
17
6
3
11
16
16
17
15
5
9
7
11
17
6
3
11
16
16
17
15
5
9
7
11
17
6
3
FLOW DAY
FLOW DAY
1.25
0.82
0.85
1.02
0.71
0.45
0.37
0.34
0.28
0.48
1.25
.87
.90
.05
.10
.44
0.85
0.48
0.40
0.31
0.23
0.54
1.90
3.34
1.59
0.91
0.93
1.22
0.74
0.42
0.34
0.28
0.20
0.45
1.59
2.72
1.30
0.79
0.79
1.02
0.65
0.40
0.31
0.28
0.20
0.42
1.30
2.15
16
21
21
21
21
21
21
21
1.27
0.93
1.93
1.08
1.61
1.08
FLOW
1.33
0.93
-------
TRIBUTARY FLOW INFORMATION FOR GEORGIA
12/2/75
LAKE CODE 1318
LAKE BURTON
MEAN MONTHLY FLOWS AND DAILY FLOWS(CMS)
TRIBUTARY
1318F1
1318ZZ
MONTH YEAR
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
MEAN FLOW DAY
2.44
1.98
2.46
1.81
0.96
0.85
0.54
0.45
0.74
1.87
1.87
1.90
3.65
3.00
3.71
2.72
1.42
1.25
0.79
0.74
1.19
2.83
2.69
2.78
11
16
16
17
15
5
9
7
11
17
6
3
FLOW DAY
2.38
1.42
1.47
1.87
1.13
0.65
0.54
0.45
0.34
0.74
2.38 21
4.13 26
FLOW DAY
FLOW
2.49
1.84
-------
APPENDIX D
PHYSICAL and CHEMICAL DATA
-------
STORET RETRIEVAL DATE 74/11/36
131801
35 itS 05.0 083 32 10.0
BURTON LAKE
13241 GEORGIA
DATE
FROM
TO
73/06/28
73/09/18
73/11/10
TIME
OF
DAY
16
16
16
16
16
16
16
11
11
11
11
11
11
11
14
14
14
14
14
40
40
40
40
40
40
40
25
25
25
25
25
25
25
30
30
30
30
30
DEPTH
FEET
0000
0005
0010
0015
0040
0080
0100
0000
0020
0030
0045
0060
0075
0090
0000
0010
0030
0060
0084
00010
WATER
TEMP
CENT
26.6
26.2
23.9
21.1
16.7
13.6
12.8
24.5
24.4
21.7
18.6
16.8
15.9
15.2
15.9
15.5
15.5
15.4
15.3
11EPALES
00300
00
MG/L
8.4
9.7
8.8
6.8
7.0
2.4
6.2
3.2
2.8
2.8
2.4
0.1
8.0
7.6
7.8
7.6
00077 00094
TRANSP CNDUCTVY
SECCHI FIELD
INCHES MICROMHO
126 50K
50K
50K
SDK
SDK
50K
50K
118 15
16
18
15
14
15
24
216 20
18
19
18
19
3
00400
PH
SU
7.00
6.90
7.10
6.80
6.40
6.40
6.30
7.10
6.30
5.60
5.40
5.30
5.30
5.70
6.40
6.40
6.40
6.30
6.40
00410
t ALK
CAC03
MG/L
10
10K
10K
10K
10K
UK
13
10K
10*
10K
10K
10K
10K
10K
10K
10K
10K
10K
10K
2111202
0105
00610
NH3-N
TOTAL
MG/L
0.100
0.060
0.060
0.060
0.070
0.080
0.170
0.050
0.040
0.040
0.040
0.040
0.040
0.200
0.050
0.050
0.040
0.060
0.060
FEET DEPTH
00625
TOT KJEL
N
MG/L
0.600
0.500
0.300
0.300
0.300
0.40*
0.300
0.800
0.500
0.400
0.300
0.200
0.200K
0.500
0.200K
0.200K
6.200K
0.200K
0.200K
00630
N021N03
N-TOTAL
MG/L
0.070
0.040
0.040
0.050
0.000
0.070
0.060
0.020
0.030
0.030
0.030
0.050
0.100
0.040
0.020
0.020
0.020
0.020
0.020
00671
PHOS-DIS
ORTHO
MG/L P
0.004
0.003
0.002
0.002
0.002
0.002
0.002K
0.006
0.0*9
0.007
0.007
0.006
0.006
0.004
K VALUE KNOWN TO BE
LESS THAN INDICATED
-------
STORET RETRIEVAL 04FE 74/11/26
DATE
FROM
TO
73/06/2«
73/09/18
73/11/10
TIM
OF
DAY
16
16
16
16
16
16
16
1
1
1
1
1
1
11
14
14
14
14
14
F
40
40
40
40
40
40
40
25
25
25
25
25
25
25
30
30
30
30
30
DEPTH
FEET
0000
0005
0010
0015
0040
0080
0100
0000
0020
0030
0045
0060
0075
0030
0000
0010
0030
0060
0034
00665
'HOS-TOT
MG/L P
0.00"
0.007
0.006
0.010
0.010
O.OJ6
0.006
0.006
0.011
0.009
32217
CMLRPHYL
A
UG/L
2.0
0.009
0.007
0.004
0.005
0.005
0.007
0.006
0.006
2.4
1.6
131801
35 43 05.0 OR3 32 10.0
BUTTON LAKF
13241 GEORGIA
11EPALES
3
2111202
0105 FEET
DEPTH
-------
STORET RETRIEVAL DATE 74/11/26
131802
35 51 10.0 083 32
BURTON LAKE
132*1 GEORGIA
05.0
DATE
FROM
TO
73/06/28
73/09/18
73/11/10
TIME DEPTH
OF
DAY FEET
17 30
17 30
17 30
17 30
17 30
12 15
12 15
12 15
12 15
14 55
14 55
14 55
14 55
0000
0010
0017
0030
0047
0000
0015
0025
0038
0000
0010
0025
0042
00010
WATER
TEMP
CENT
27.0
26.0
21.6
18.1
16.2
24.4
24.2
22.2
19.6
15.7
15.4
15.2
15.2
00300 00077 00094
00 TRANSP CNDUCTVY
SECCHI FIELD
MG/L INCHES MICROMHO
97
8.9
8.2
5.7
2.1
7.8 112
7.4
4.8
0.4
144
7.6
8.0
8.2
50K
50K
50K
50K
50K
16
15
16
18
18
17
18
17
11EPALES
3
00400 00410
PH T ALK
CAC03
SU
7.10
7.10
6.50
6.30
6.30
6.50
6.20
5.70
5.70
6.40
6.50
6.30
6.30
MG/L
10K
10K
10
11
10K
10K
10K
10K
10K
10
10K
10K
10K
2111202
0051 FEET DEPTH
00610 00625 00630 00671
NH3-N TOT KJEL N021N03 PHOS-OIS
TOTAL N N-TOTAL ORTHO
MG/L
0.070
0.060
0.060
0.060
0.110
0.040
0.040
0.060
0.130
0.060
0.040
0.050
0.040
MG/L MG/L
0.300
0.200
0.400
0.20IK
0.20PK
0.500
0.500
0.400
0.400
0.300
0.200K
0.200K
0.20 OK
.040
.040
.•SO
.•60
.060
.•20
.040
.•40
.•30
.030
.020
.•20
.•30
MG/L P
0.002
0.002
O.M2
0.192
0.6*2
• .••6
•••04
O.H6
O.M4
K VALUE KNOWN TO BE
LESS THAN INDICATED
-------
STORE! RETRIEVAL DATE 74/11/26
00665 32217
DATE TIME DEPTH PHOS-TOT CHLRPHYL
FROM OF A
TO DAY FEET MG/L P UG/L
73/06/28 17 30 0000 0.007 5.7
17 30 0010 0.009
17 30 0017 0.009
17 30 0030 0.009
17 30 0047 0.014
73/09/1H 12 15 0000 0.005 3.7
12 15 0015 0.006
12 15 0025 0.024
12 15 0038 0.006
73/11/10 14 55 0000 0.007 1.3
14 55 0010 0.006
14 55 0025 0.007
14 55 0042 0.007
131802
35 51 10.0 083 32 05.0
BURTON LAKE
13241 GEORGIA
11EPALES
3
2111202
0051 FEET
DEPTH
-------
STORE! RETRIEVAL DATE 74/11/26
131803
35 51 20.0 083 33 00.
BURTON LAKE
13241 GEORGIA
DATE
FROM
TO
73/06/28
73/09/18
73/11/10
00010
TIME DEPTH WATER
OF TEMP
DAY FEET
18
18
18
18
18
12
12
12
1?
15
15
15
15
05
05
05
05
05
50
50
50
50
15
15
15
15
0000
0010
0017
0035
0050
0000
0015
0030
0050
0000
0010
0025
0048
CENT
26.7
26.5
25.4
17.3
15.8
24.4
24.1
21.0
17.4
15.6
15.1
14.9
14.7
11EPALES
00300
DO
MG/L
10.1
8.2
7.2
6.8
a.o
7.6
4.2
0.6
7.2
8.4
8.4
00077
TRANSP
SECCHI
INCHES
106
110
196
00094
CNDUCTVY
FIELD
MICROMHO
50K
50K
50K
50K
50K
16
16
17
20
18
18
18
17
3
00400
PH
SU
7.10
7.10
6.50
6.50
6.40
6.30
6.10
5.90
5.80
6.30
6.50
6.40
6.50
00410
T ALK
CAC03
MG/L
10K
10K
10K
10K
10K
10K
10K
10K
13
11
10K
10K
10K
2111202
0055
00610
NH3-N
TOTAL
MG/L
0.060
0.060
0.070
0.060
0.080
0.040
0.040
0.070
0.170
0.050
0.040
0.040
0.040
FEET DEPTH
00625
TOT KJEL
N
MG/L
0.200
0.200K
0.200K
0.200K
0.200K
0.200
0.200K
0.200K
0.300
0.200K
0.200K
0.200K
0.200K
00630
NO2&N03
N-TOTAL
MG/L
0.050
0.050
0.050
0.070
0.080
0.030
0.030
0.060
0.050
0.020
0.020
0.020
0.020
00671
PHOS-OIS
ORTHO
MG/L P
\
0.003
0.002K
0.002
0.002
0.002
0.005
0.008
0.004
0.006
K VALUE KNOWN TO BE LESS
THAN INDICATED
-------
STORE! RETRIEVAL DATE 74/11/26
00665 32217
DATE TIXE DEPTH PHOS-TOT CHLRPHYL
FROM OF A
TO DAY FEET MG/L P UG/L
73/06/28 18 05 0000 0.007 2.8
Ifl 05 0010 0.007
18 05 0017 0.009
18 05 0035 0.009
18 05 0050 0.009
73/09/18 12 50 0000 O.OOrt 3.0
12 50 0015 0.011
12 50 0030 0.007
12 50 0050 0.015
73/11/10 15 15 0000 0.006 2.1
15 15 0010 0.010
15 15 0025 0.005
15 15 0048 0.008
131803
35 51 20.0 083 33 00.0
BURTON LAKE
13241 GEORGIA
11EPALES
3
2111202
0055 FEET
DEPTH
-------
APPENDIX E
TRIBUTARY DATA
-------
STORE! RETRIEVAL DATE 75/12/02
1318A1 1318AI
34 53 30.0 083 32 00.0
TALLULAH RIVER
13145 RABUN CO HWY NAP
I/LAKE BURTON
TALLULAH RIVER RO N END OF LAKE
11EPALES 2111204
4 0000 FEET DEPTH
DATE
FROM
TO
73/03/11
73/04/16
73/05/16
73/06/17
73/07/15
73/08/05
73/09/09
73/10/07
73/11/11
73/12/17
74/01/06
74/01/21
74/02/03
74/02/21
TIME DEPTH
OF
DAY FEET
12 25
12 15
11 40
11 34
11 50
11 35
09 45
12 00
10 30
14 00
12 37
14 30
11 00
13 35
00630
N02&N03
N-TOTAL
MG/L
0.042
0.039
0.010K
0.013
0.063
0.066
0.056
0.034
0.046
0.168
0.040
0.048
0.060
0.040
00625
TOT KJEL
N
MG/L
1.100
1.000
0.100K
0.150
0.200
0.100K
0.810
0.100K
0.400
0.100K
1.000
0.900
1.200
0.100K
00610
NH3-N
TOTAL
MG/L
0.115
0.039
0.007
0.021
0.014
0.016
0.097
0.014
0.018
0.008
0.005
0.040
0.035
0.010
00671
PHOS-DIS
ORTHO
MG/L P
0.005K
0.005K
0.005K
0.005K
0.008
0.015
0.005K
0.010
0.005K
0.005K
0.005
0.010
0.005
0.005K
00665
PHOS-TOT
MG/L P
0.010
0.005K
0.005K
0.005K
0.020
0.015
0.030
0.015
0.005K
0.005
0.010
0.010
0.055
0.005K
K VALUE KNOWN TO BE
LESS THAN INDICATED
-------
STORET RETRIEVAL DATE 75/12/02
1318A2 1318A2
34 47 30.0 083 32 30.0
TALLULAH
13 RABUN CO HXY MAP
0/LAKE BURTON
ST RT S 880 BRDG BELO DAM S END OF LAKE
11EPALES 2111204
4 0000 FEET DEPTH
DATE
FROM
TO
73/03/11
73/04/16
73/05/16
73/06/17
73/07/15
73/08/05
73/09/09
73/10/07
73/11/11
73/12/17
74/01/06
74/01/21
74/02/03
74/02/21
TIME DEPTH
OF
DAY FEET
14 30
14 05
13 15
12 20
13 00
12 45
11 30
11 15
13 30
15 10
13 06
16 15
11 45
14 15
00630
N02&N03
N-TOTAL
MG/L
0.040
0.032
0.017
0.026
0.132
0.056
0.046
0.030
0.016
0.112
0.044
0.020
0.064
0.048
00625
TOT KJEL
N
MG/L
1.260
0.780
0.170
0.100K
0.360
0.170
1.000
0.200
0.100K
0.200
0.100K
0.100K
0.200
0.100K
00610
NH3-N
TOTAL
MG/L
0.077
0.030
0.007
0.042
0.061
0.080
0.460
0.131
0.030
0.028
0.035
0.025
0.025
0.045
00671
PHOS-DIS
ORTHO
MG/L P
0.005K
0.005K
0.005K
0.005K
0.006
0.006
0.005K
0.007
0.005K
0.005K
0.005K
0.005
0.005K
0.005K
00665
PHOS-TOT
MG/L P
0.005K
0.005K
0.005K
0.005K
0.006
0.010
0.005K
0.007
0.005K
0.010
0.015
0.007
0.010
0.005K
K VALUE KNOWN TO BE
LESS THAN INDICATED
-------
STORET RETRIEVAL DATE 75/12/02
131881 131881
34 49 30.0 083 35 30.0
WILDCAT CREEK
13 RABUN CO HWY HAP
T/LAKE BURTON
HWY 197 8ROO N OF LA PRAOES CAMP
11EPALES \ 2111204
4 . 0000 FEET DEPTH
DATE
FROM
TO
73/03/11
73/04/16
73/05/16
73/06/17
73/07/15
73/08/05
73/09/09
73/10/07
73/11/11
73/12/17
74/01/06
74/01/16
74/02/03
74/02/21
TIME DEPTH
OF
DAY FEET
10 40
10 45
10 00
10 10
11 00
10 45
08 45
12 50
09 40
13 20
11 20
13 00
10 00
12 20
00630
N02&N03
N-TOTAL
MG/L
0.023
0.010K
0.010K
0.010K
0.031
0.010K
0.011
0.010K
0.011
0.064
0.008
0.016
0.020
0.016
00625
TOT KJEL
N
MG/L
2.050
0.690
0.100K
0.100K
0.160
0.100K
0.910
0.100K
0.450
0.100K
0.400
0.100K
0.300
0.100K
00610
NH3-N
TOTAL
MG/L
0.088
0.030
0.011
0.014
0.019
0.011
0.520
0.021
0.020
0.016
0.015
0.020
0.082
0.010
00671
PHOS-DIS
ORTHO
MG/L P
0.005K
0.005K
0.005K
0.005K
0.008
0.006
0.005K
0.008
0.005K
0.005K
0.005K
0.005
0.005K
0.005K
00665
PHOS-TOT
MG/L P
0.010
0.005K
0.005K
0.010
0.015
0.012
0.010
0.008
0.005K
0.005K
0.005
0.005K
0.015
0.005K
K VALUE KNOWN TO BE
LESS THAN INDICATED
-------
STORET RETRIEVAL DATE 75/12/02
131HC1 1318C1
34 50 30.0 083 35 30.0
MOCCASIN CREEK
13 RABUN CO H*Y MAP
T/LAKE BURTON
BANK BELO LK BURTON ST FISH HATCHERY
11EPALES 2111204
4 0000 FEET DEPTH
DATE
FROM
TO
73/03/11
73/04/16
73/05/16
73/06/17
73/07/15
73/08/05
73/09/09
73/10/07
73/11/11
73/12/17
74/01/06
74/01/21
74/02/03
74/02/21
00630 00625
TIME DEPTH N02&N03 TOT KJEL
OF N-TOTAL N
DAY FEET
11
10
10
10
11
10
09
12
09
13
11
13
10
12
00
50
10
20
05
50
00
45
45
25
45
35
10
35
MG/L
0
0
0
0
0
0
0
0
0
0
0
.021
.013
.010K
.011
.024
.017
.018
.016
.025
.048
.004
0.004
0
0
.028
.016
MG/L
0.
1.
0.
0.
0.
0.
1.
0.
0.
0.
0.
0.
0.
0.
740
400
100K
100K
280
100K
540
662
250
100K
100K
600
100K
200
00610 00671 00665
NH3-N PHOS-DIS PHOS-TOT
TOTAL ORTHO
MG/L
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
o.
0.
0.
039
073
028
034
067
038
120
098
091
012
015
025
015
010
MG/L
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
p
005K
012
005K
005K
010
010
017
021
032
005K
005K
010
005K
005K
MG/L P
0.015
0.020
0.010
0.015
0.015
0.020
0.030
0.022
0.035
0.005K
0.005
0.010
0.005
0.005K
K VALUE KNOWN TO BE
LESS THAN INDICATED
-------
STORE! RETRIEVAL DATE 75/12/02
131801 131801
34 51 30.0 083 35 00.0
DICKS CREEK
13 RABON CO HWY MAP
I/LAKE BURTON
ST RO 874 BROG 1 MI N LN BURTON HATCHERY
11EPALES 21112*4
4 oeoe FCCT DEPTH
DATE
FROM
TO
73/03/11
73/04/16
73/05/16
73/06/17
73/07/15
73/08/05
73/09/09
73/10/07
73/11/11
73/12/17
74/01/06
74/01/21
74/02/03
74/02/21
TIME DEPTH
OF
DAY FEET
11 15
11 05
10 30
10 40
11 12
11 00
09 10
12 35
10 00
13 30
12 05
13 50
10 20
12 41
00630
N02&N03
N-TOTAL
MG/L
0.014
0.010K
0.010K
0.010K
0.024
0.010K
0.010K
0.010K
0.010K
0.004
0.004
0.024
0.008
0.008
00625
TOT KJEL
N
MG/L
1.800
0.100K
0.100K
0.100K
0.150
0.100K
0.630
0.450
0.350
0.100K
0.100K
0.400
0.150
0.100K
00610
NH3-N
TOTAL
MG/L
0.081
0.011
0.005K
0.010
0.024
0.008
0.280
0.067
0.019
0.005K
0.015
0.020
0.020
0.010
00671
PHOS-DIS
ORTHO
MG/L P
0.005K
0.005K
0.005K
0.008
0.005K
0.005K
0.008
0.005K
0.005K
0.005K
0.005K
0.005K
0.005K
00665
PHOS-TOT
MG/L P
0.015
0.005K
0.005K
0.010
0.010
0.010
0.005K
0.025
0.005K
0.005K
0.005
0.005K
0.020
0.005K
K VALUE KNOWN TO BE
LESS THAN INDICATED
-------
STORET RETRIEVAL DATE 75/12/02
131BE1 1318E1
34 53 00.0 083 33 00.0
POPCORN CREEK
13 RABUN CO HMY MAP
T/LAKE BURTON
BANK ABOVE CONFLUENCE WITH LAKE
11EPALES 2111204
4 0000 FEET DEPTH
DATE
FROM
TO
73/03/11
73/04/16
73/05/16
73/06/17
73/07/15
73/08/05
73/09/09
73/10/07
73/11/11
73/12/17
74/01/06
74/01/21
74/02/03
74/02/21
00630 00625
TIME DEPTH N02&N03 TOT KJEL
OF N-TOTAL N
DAY FEET
12
11
11
11
11
11
09
12
10
13
12
14
10
13
00
35
00
08
30
20
30
20
10
45
15
10
40
05
MG/L
0
0
0
0
0
0
0
0
0
0
0
0
0
0
•
•
•
*
•
*
•
•
*
•
•
•
*
•
014
010K
010K
010K
023
010K
013
010K
010K
020
004
016
008
004
MG/L
1.
0.
0.
0.
0.
0.
1.
0.
0.
0.
0.
0.
0.
0.
470
280
100K
100K
180
100K
300
150
100K
300
100K
300
200
100K
00610 00671 00665
NH3-N PHOS-DIS PHOS-TOT
TOTAL ORTHO
MG/L
0.081
0.017
O.OOSK
0.014
0.013
0.006
0.670
0.050
0.014
0.008
0.010
0.040
0.050
0.010
MG/L
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
P
005K
005K
005K
005K
005
005K
005K
009
005K
005K
005K
005
005K
005K
MG/L P
0.010
0.010
O.OOSK
0.010
0.010
O.OOSK
O.OOSK
0.010
O.OOSK
O.OOSK
0.010
O.OOSK
0.020
O.OOSK
K VALUE KNOWN TO BE
LESS THAN INDICATED
-------
STORET RETRIEVAL DATE 75/12/02
1318F1 1318F1
34 51 30.0 083 30 30.0
TIHPSON CREEK
13 RA8UN CO HMY HAP
T/LAKE BURTON
BITUMINOUS RO BROG .2 HI S JCT HMY 76
HEPALES 2111204
4 0000 FEET DEPTH
DATE
FROM
TO
73/03/11
73/04/16
73/05/16
73/06/17
73/07/15
73/08/05
73/09/09
73/10/07
73/11/11
73/12/17
74/01/06
74/01/21
74/02/03
74/02/26
TIME DEPTH
OF
DAY FEET
12 50
12 40
12 50
12 01
12 40
12 30
11 30
11 30
11 10
15 30
12 50
14 50
11 20
14 00
00630
N02&N03
N-TOTAL
MG/L
0.088
0.038
0.029
0.046
0.092
0.046
0.031
0.042
0.020
0.036
0.084
0.052
0.068
0.100
00625
TOT KJEL
N
MG/L
3.570
0.180
0.100K
0.100K
0.245
0.100K
1.000
0.750
0.100K
0.100K
0.100K
1.100
0.100
0.300
00610
NH3-N
TOTAL
MG/L
0.093
0.008
0.005K
0.008
0.015
0.006
0.460
0.072
0.018
0.012
0.010
0.050
0.015
0.030
00671
PHOS-DIS
ORTHO
MG/L P
0.005K
0.005K
0.005K
0.005K
0.015
0.006
0.005K
0.009
0.005K
0.005K
0.005K
0.010
0.005
0.010
00665
PHOS-TOT
MG/L P
0.030
0.020
0.015
0.020
0.040
0.020
0.020
0.020
0.005K
0.010
0.020
0.025
0.065
0.050
K VALUE KNOWN TO BE
LESS THAN INDICATED
------- |