U.S. ENVIRONMENTAL PROTECTION AGENCY
NATIONAL EUTROPHICATION SURVEY
WORKING PAPER SERIES
REPORT
ON
TBIKILLER FERRY RESERVOIR
CHEROKEE AND SEQUOYAH COUNTIES
OKLAHOm
EPA REGION VI
v
WORKING PAPER No, 593
CORVALLIS ENVIRONMENTAL RESEARCH LABORATORY - CORVALLIS, OREGON
and
ENVIRONMENTAL MONITORING & SUPPORT LABORATORY - LAS VEGAS, NEVADA
699-440
-------
REPORT
ON
TENKILLER FERRY RESERVOIR
CHEROKEE AND SEQUOYAH COUNTIES
OKLAHOW
EPA REGION VI
WORKING PAPER No, 593
WITH THE COOPERATION OF THE
OKLAHOMA DEPARTMENT OF POLLUTION CONTROL
AND THE
OKLAHOMA NATIONAL GUARD
I^RCH, 1977
-------
REPORT ON TENKILLER FERRY RESERVOIR
CHEROKEE AND SEQUOYAH COUNTIES, OKLAHOMA
EPA REGION VI
by
National Eutrophication Survey
Water and Land Monitoring Branch
Monitoring Applications Laboratory
Environmental Monitoring & Support Laboratory
Las Vegas, Nevada
and
Eutrophication Survey Branch
Con/all is Environmental Research Laboratory
Corvallis, Oregon
Working Paper No. 593
OFFICE OF RESEARCH AND DEVELOPMENT
U.S. ENVIRONMENTAL PROTECTION AGENCY
MARCH 1977
-------
CONTENTS
Page
Foreword i i
List of Oklahoma Study Lakes iv
Lake and Drainage Area Map v
Sections
I. Conclusions 1
II. Lake and Drainage Basin Characteristics 3
III. Lake Water Quality Summary 5
IV. Nutrient Loadings 11
V. Literature Reviewed 17
VI. Appendices 18
-------
ii
FOREWORD
The National Eutrophicafion Survey was Initiated in 1972 in
response to an Administration commitment to investigate the nation-
wide threat of accelerated eutrophlcation to freshwater lakes and
reservoirs.
OBJECTIVES
The Survey was designed to develop, in conjunction with state
environmental agencies, information on nutrient sources, concen-
trations, and impact on selected freshwater lakes as a basis for
formulating comprehensive and coordinated national, regional, and
state management practices relating to point source discharge
reduction and nonpoint source pollution abatement in lake water-
sheds.
ANALYTIC APPROACH
The mathematical and statistical procedures selected for the
Survey's eutrophication analysis are based on related concepts
that:
a. A generalized representation or model relating
sources, concentrations, and impacts can be
constructed.
b. By applying measurements of relevant parameters
associated with lake degradation, the generalized
model can be transformed into an operational
representation of a lake, its drainage basin, and
related nutrients.
c. With such a transformation, an assessment of the
potential for eutrophication control can be made.
LAKE ANALYSIS
In this report, the first stage of evaluation of lake and
watershed data collected from the study lake and its drainage
basin is documented. The report is formatted to provide state
environmental agencies with specific information for basin
planning [§303(e)]» water qualitv criteria/standards review
L§303(c]], clean lakes [§314(a,b)], and water quality monitoring
[§106 and §305(b)] activities mandated by the Federal Water
Pollution Control Act Amendments of 1972.
-------
Ill
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.
ACKNOWLEDGMENTS
The staff of the National Eutrophication Survey (Office of
Research and Development, U.S. Environmental Protection Agency)
expresses sincere appreciation to the Oklahoma Department of
Pollution Control for professional involvement, to the Oklahoma
National Guard for conducting the tributary sampling phase of the
Survey, and to those Oklahoma wastewater treatment plant operators
who provided effluent samples and flow data.
Dr. Denver Talley, Director, Oklahoma Department of Pollution
Control; the staff of the Oklahoma Water Resources Board; and the
staff of the Oklahoma State Department of Health reviewed the pre-
liminary reports and provided critiques most useful in the prepara-
tion of this Working Paper Series.
Major General John Coffey, Jr., the Adjutant General of
Oklahoma, and Project Officers Colonel Curtis W. Milligan and
Major James 0. Haney, Jr., who directed the volunteer efforts of
the Oklahoma National Guardsmen, are also gratefully acknowledged
for their assistance to the Survey.
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IV
NATIONAL EUTROPHICATION SURVEY
STUDY LAKES
STATE OF OKLAHOMA
LAKE NAME
Altus Reservoir
Arbuckle Lake
Lake Elsworth
Lake Eufaula
Fort Cobb Reservoir
Fort Supply Reservoir
Foss Dam Reservoir
Lake Frances
Grand Lake 0' The Cherokees
Lake Hefner
Keystone Reservoir
Oologah Lake
Tenkiller Ferry Reservoir
Lake Thunderbird
Wister Reservoir
COUNTY
Greer, Kiowa
Murray
Caddo, Comanche
Haskell, Mclntosh,
Okmulgee, Pittsburg
Caddo
Woodward
Custer
Adair
Mayes, Delaware, Craig,
Ottowa
Oklahoma
Tulsa, Creek, Osage, Pawnee
Nowata, Rogers
Cherokee, Sequoyah
Cleveland
LeFlore
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rr~ s f -•
TENKILLER FERRY RESERVOIR
Tributary Sampling Site
X Lake Sampling Site
Sewage Treatment Facility
^3 Drainage Area Boundary
TENKILLER
FERRY
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REPORT ON TENKILLER FERRY RESERVOIR, OKLAHOMA
STORE! NO. 4013
I. CONCLUSIONS
A. Trophic Condition:*
Based upon Survey data, Tenkiller Ferry Reservoir is
considered eutrophic, i.e., nutrient rich and highly pro-
ductive. Whether such nutrient enrichment is to be consi-
dered beneficial or deleterious is determined by its actual
or potential impact upon designated beneficial water uses
of each lake.
Chlorophyll a_ values in the lake ranged from 0.1 yg/1
to 24.6 yg/1 with a mean of 6.6 yg/1. Potential for primary
productivity as measured by algal assay control yield was
high. Of the 16 Oklahoma lakes sampled in 1974 (including
Lake Texoma), 10 had greater median total phosphorus, 4 had
greater median inorganic nitrogen, and 7 had greater median
orthophosphorus levels than Tenkiller Ferry Reservoir.
Survey limnologists did not report any problem conditions
during their visits to the lake.
*See Appendix E.
-------
B. Rate-Limiting Nutrient:
The algal assay results indicate that Tenkiller Ferry Reser-
voir was limited by available phosphorus at the time the autumn
assay sample was collected. The lake data suggest primary limi-
tation by phosphorus at all other sampling times as well.
C. Nutrient Controllability:
1. Point sources -
Point sources were estimated to contribute 15.5% of the
total phosphorus load during the sampling year. The towns
of Tahlequah and Stilwell contributed 8.0% and 6.5%, respec-
tively. Westville was estimated to contribute 1.0%.
The calculated annual phosphorus loading of 2.13 g P/
m^/yr is approximately twice that proposed by Vollenweider
(1975) as "eutrophic" for a lake with such volume and reten-
tion time. Although elimination of all point source phos-
phorus loads would not reduce this annual loading to Vollen-
weider's "eutrophic" level (0.92 g P/m2/yr), it would reduce
the potential for the occurrence of nuisance conditions.
2. Nonpoint sources -
It is calculated that nonpoint sources contributed 84.5%
of the total phosphorus input to Tenkiller Ferry Reservoir
during the sampling year. Gaged tributaries contributed 71.1%
of the total, and ungaged drainage areas were estimated to
have contributed 12.6%.
-------
II. LAKE AND DRAINAGE BASIN CHARACTERISTICS
Lake and drainage basin characteristics are itemized below.
Lake surface area and mean depth were provided by the Oklahoma
Department of Pollution Control; maximum depth was provided by
the Oklahoma Water Resources Board, Tributary flow data were
provided by the Oklahoma District Office of the U.S. Geological
Survey (USGS). Outlet drainage area includes the lake surface
area. Mean hydraulic retention time was obtained by dividing
the lake volume by mean flow of the outlet. Precipitation values
are estimated by methods as outlined in National Eutrophication
Survey (NES) Working Paper No. 175. A table of metric/English
conversions is included as Appendix A.
A. Lake Morphometry:
1. Surface area: 51.19 km2.
2. Mean depth: 15.5 meters.
3. Maximum depth: 46.3 meters.
4. Volume: 793.445 x 106 m3.
5. Mean hydraulic retention time: 240 days.
-------
B. Tributary and Outlet:
(See Appendix B for flow data)
1. Tributaries -
Drainage Mean Flow
Name areaCkm2) (m3/sec)
A-2 Illinois River 2,483.8 23,68
C-l Barren Fork 795,1 8.45
Minor tributaries and
immediate drainage - 839.8 9.04
Totals 4,118.7 41.17
2. Outlet - A-l Illinois River 4,169,9 38.32
C. Precipitation:
1. Year of sampling: 137.3 cm.
2. Mean annual: 113.1 cm.
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III. LAKE WATER QUALITY SUMMARY
Tenkiller Ferry Reservoir was sampled four times during the
open-water season of 1974 by means of a pontoon-equipped Huey
helicopter. Each time, samples for physical and chemical para-
meters were collected from four 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 station
for chlorophyll a_ analysis and phytoplankton identification and
enumeration. During the first and last visits, 18.9-liter depth-
integrated samples were composited for algal assays. Maximum
depths sampled were 44.5 meters at Station 01, 36.9 meters at
Station 02, 26.2 meters at Station 03, and 15.2 meters at Station
04. 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 maxi-
mum depth for each site. Results of the phytoplankton counts and
chlorophyll ^determinations are included in III-B. Results of
the limiting nutrient study are presented in III-C.
-------
TENMLLEr) KERRY *tSK*VOI
COLit "013
PHYSICAL AND CHEMICAL CHARACTERISTICS
PARAMETER
TgMPEWATUVt. (DEG CENT)
O.-l.'- M DEPTH
MAX DEPTH*1"
DISSOLVED OXYGEN (MG/L
O.-l.S M r.EPTH
MAX DEPTH***
CONDUCTIVITY (UMH05)
O.-l .5 M DEPTH
MAX DEPTH*"
Ph (STANDAhU UNITS)
O.-l.S M uEPTH
MAX DEPTH*"
TOTAL ALKALINITY (Mi?/L
O.-l.^ M 1,'fc.PTn
MAX OEPTH«»
TOTAL P (MG/L)
O.-l.S M DEPTH
MAX. DEPTHoo
N*
8
4
)
4
4
8
4
8
4
)
M
4
8
4
( 4/ 3/74
S«»» = 4
RANGE MEDIAN
11.2- 15.3
8.0- 13.6
9.0- 10.4
8.6- 9.0
119.- 154.
104.- 150.
7.6- 7.8
7.1- 7.5
53.- 77.
65.- 83.
0.039-0.051
.0.055-0.199
12.3
9.5
10.1
8.9
129.
124.
7.8
7.2
74.
73.
0.044
0.070
)
MAX
DEPTH
OANGE
fc
4
4
4
8
4
8
4
7
4
8
4
( 6/14/74
S»»« = 4
RANGE MEDIAN
24.3- 25.8
13.5- 20.4
8.0- 10.8
0.6- 5.2
168.- 179.
119.- 148.
8.4- 9.0
7.2- 7.4
72.- 86.
40.- 90.
0.020-0.040
0.049-0.232
25.6
17.4
9.7
2.9
173.
140.
8.9
7.3
78.
08.
0.02H
0.162
)
MAX
DEPTH
KANGE
(METERS)
0.0-
15.2-
1.5-
15.2-
0.0-
15.2-
0.0-
15.2-
0.0-
15.2-
0.0-
15.2-
1.5
44.5
1.5
44.5
US
44.5
1.5
44.5
1.5
44.5
1.5
44.5
N»
4
4
4
4
4
4
4
4
4
4
4
4
( 8/30/74 ]
S»»» = 4
RANGE MEDIAN
27.0- 27.4
18.2- 26.3
5.2- 7.0
0.0- 3.2
142.- 183.
125.- 201.
7.8- 8.3
7.3- 7.6
75.- 82.
78.- 92.
O.OjO-0.067
0.130-0.347
27.1
21.1
6.5
0.4
156.
162.
8.2
7.4
76.
88.
0.036
0.163
i
MAX
DEPTH
RANGE
-------
RESEKvOI
^ TO ->ET CODE Hi
• PHYSICAL AND CHEMICAL CHARACTERISTICS
( 10/21/7* )
4
TOTAL ALKALINITY (MG/L)
0.-1.5 * '^t^Tn ei
t 4
TOTAL P (M&/L)
O.-l.H N1 OEPTH o
DISSCLVEU OKTnO P (MG/L)
IV.6 19.5 0.0- 1.5
19.2 18. 1 i'1.4- a 1.5
10.0 7.o 0.0- 1.5
7.4 4.1 10.4- 41.5
8 145.- 147. 145. 0.0- 1.5
4 155.- 189. 1ft1. 10.4-41.5
7.2- 8.5 7.7 0.0- 1.5
6.9- 7.4 7.1 10.4- 41.5
/!.- HO. 74. 0.0- 1.5
80.- 91. 46. 10.4- 41.5
0.0^0-0.052 0.02s 0.0- 1.5
0.0*5-0. 154 0.11J 10.4- rri
AMMONIA
MA* j£PTri««
SfcCCHI OliC (YtT£^S)
8 0.003-0.007 0.004 0.0- 1.5
4 0.005-0.019 O.Olb 10.4- 41.5
d 0.200-0.350 0.240 0.0- 1.5
<• 0.220-0.650 0.360 in.4- 41.5
0.020-0.040 0.025 0.0- 1.5
0.020-0.920 0.175 10.4- 41.5
0.200-0.600 0.350 0.0- 1.5
0.200-1.200 0.400 10.4- 41.5
1.2- 1.6 1.3
* N = fiO. OF
»a -^AKlMilM Ut^TH oAMPL.EO AT EACH SITE
»oo s r NO. OF srrts SAMPLED ON T^IS OATE
-------
B. Biological Characteristics:
1. Phytoplankton -
04/03/74
06/14/74
08/'30/74
10/21/74
Algal
Dominant Units
Genera per ml
1. Stephanodiscus 1,685
2. Melosira 481
3. Chroomonas 289
4. Cyclotella 96
5. Cryptomonas 48
Other genera 145
Total . 2,744
1. Cyclotella 369
2. Melosira 276
3, Cryptomonas 184
4. Chlamydomonas 46
Other genera —
Total 875
1. Achnanthes 873
2. Raphidiopsis 457
3. Synedra 416
4. Stephanodiscus 374
5., Nitzschia 333
Other genera 666
Total 3,119
1. Melosira 1; ,707
2. Cyclotella 443
3. Ghroomonas 316
4. Ankistrodesmus 253
5. Tetraedron 190
Other genera 695
Total 3,604
-------
2. Chlorophyll a_ -
Sampling Station Chlorophyll
Date Number (yg/1)
04/03/74 01 2.9
02 4.9
03 7.1
04 7.0
06/14/74 01 0.1
02 0.2
03 0.3
04 0.7
08/30/74 01 6.6
02 5.7
03 6.6
04 12.0
10/21/74 01 6.1
02 7.1
03 14.4
04 24.6
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TO
Ortno P
Cone, (mg/1)
0,02Q:
0.070
0.070
0.020
Inorganic N'
Conc.(mg/li)
0,320
0.320
1.320
1.32Q
Maximum Yield
(mg/1 -dry wt,)
5.2
10.0
19'.&
5.5
C. Limiting Nutrient Study:
1. Autoclaved, filtered, and nutrient spiked - 10/21/74
Spike(mg/l)
Control
0.05 P
0.05 P + 1.0 N
1.00 N
2. Discussion. -
The control yield of the assay alga, Selenastrum capri-
cornutum, indicates that the potential primary productivity
, in Tenkiller Ferry Reservoir was high, at the time of autumn
sampling.. There was a significant increase in yield over
that of the control when, orthophosphorus was added, indicat-
ing phosphorus limitation at that time. The addition of
nitrogen1 alone did not result in an increase in yield over
that of the control, and the simultaneous, addition of the
two nutrients produced the maximum increase in yield.
There is no spring assay available for Tenki liter Ferry
Reservoir. However, mean inorganic nitrogen to orthophos-
phorus (N/P) ratios in the lake were T7/1 or greater on all:
sampling occasions, further suggesting' primary limitation
by phosphorus..
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11
IV. NUTRIENT LOADINGS
(See Appendix D for data)
For the determination of nutrient loadings, the Oklahoma
National Guard collected monthly near-surface grab samples from
each of the tributary sites indicated on the map (pagev), except
for the high runoff months of April and May when two samples were
generally collected. Sampling was begun in November 1974, and
was completed in October 1975.
Through an interagency agreement, stream flow estimates for
the year of sampling and a "normalized" or average year were pro-
vided by the Oklahoma District Office of the USGS for the tribu-
tary sites nearest the lake.
In this report, nutrient loads for sampled tributaries were
determined by using a modification of a USGS computer program for
calculating stream loadings. Nutrient loads indicated for tribu-
taries are those measured minus known point source loads, if any.
Nutrient loadings for unsampled "minor tributaries and imme-
diate drainage" ("II" of USGS) were estimated by using the mean
annual concentrations in Pine Branch Creek at Station B-l and mean
annual ZZ flow.
The operators of the Stilwell and Tahlequah wastewater treat-
ment plants provided monthly effluent samples and corresponding
flow data. Nutrient loads for the city of Westville wastewater
treatment plant were estimated at 1.134 kg P and 3.401 kg N/capita/
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12
A. Waste Sources:
1. Known municipal -
Name
Stilwell
Tahlequah
Westville
Pop.*
Served
3,000
10,500
1,000
Treatment*
Trickling
filter
Activated
sludge
Trickling
filter
Mean Flow
(m3/d x 103)
2.231
3.679
0.378**
Receiving
Water
Caney Creek/
Illinois River
Ross Branch/
Illinois River
Shell Branch/
Barren Fork
2. Known industrial -
Name
Allen Canning
Company
Stilwell
Cannery
Product
Treatment
Canned . ?
vegetables
Canned Landfill
vegetables disposal
Mean Flow
(m3/d x IP3)
Receiving
Water
Tar Creek
Caney Creek/
Illinois River
*Treatment plant questionnaires; U.S.EPA, 1971.
**Estimated at 0.3785 m3/capita/day.
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13
B. Annual Total Phosphorus Loading - Average Year:
1. Inputs -
% of
Source kg P/yr total
a. Tributaries (nonpoint load) -
A-2 Illinois River 68,875 63.2
C-l Barren Fork 8,605 7.9
b. Minor tributaries and immediate
drainage (nonpoint load) - 13,685 12.6
c. Known municipal STP's -
Stilwell 7,110 6.5
Tahlequah 8,725 8.0
Westville 1,135 1.0
d. Septic tanks* - 20 <0.1
e. Known industrial -
Allen Canning Company Unknown —
Stilwell Cannery Unknown —
f. Direct precipitation** - 895 0.8
Totals 109,050 100.0
2. Output - A-l Illinois River 59,305
3. Net annual P accumulation - 49,745
*Estimate based on 40 lakeside residences and 8 parks.
**Estimated (see NES Working Paper No. 175).
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14
C. Annual Total Nitrogen Loading - Average Year:
1. Inputs -
% of
Source kg N/yr total
a. Tributaries (nonpoint load) -
A-2 Illinois River 1,750,390 67.4
C-l Barren Fork 434,890 16.8
b. Minor tributaries and immediate
drainage (nonpoint load) - 321,290 12.4
c. Known municipal STP's -
- Stilwell 12,995 0.5
Tahlequah 18,015 0.7
Westville 3,400 0.1
d. Septic tanks* - 705 <0.1
e. Known industrial -
Allen Canning Company Unknown —
Stilwell Cannery Unknown —
f. Direct precipitation** - 55.265 2.1
Totals 2,596,950 100.0
2. Output - A-l Illinois River 2,070,280
3. Net annual N accumulation - 526,670
*Estimate based on 40 lakeside residences and 8 parks.
**Estimated (see NES Working Paper No. 175).
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15
D. Mean Annual Nonpoint Nutrient Export by Subdrainage Area:
Tributary kg P/km2/yr kg N/km?/yr
Illinois River
Barren Fork
28
11
705
547
E. Mean Nutrient Concentrations in Ungaged Streams:
Tributary
B-l Pine Branch Creek
Mean Total P
(mg/1)
0.048
Mean Total N
(mg/1)
1.127
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16
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 be applicable to water
bodies with very short 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 Tenkiller Ferry Reservoir 2.13
Vollenweider's "eutrophic" loading 0.92
Vollenweider's "oligotrophic" loading 0.46
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17
V. LITERATURE REVIEWED
U.S. Environmental Protection Agency. 1971. "Inventory of Waste-
water Treatment Facilities". EPA Publication No. OWP-1, Vol. 6.
Office of Media Programs, Office of Water Programs, Washington,
D.C.
U.S. Environmental Protection Agency. 1975. National Eutrophi-
cation 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 Special
Reference to the Phosphorus Loading Concept in Limnology.
Schweiz. Z. Hydrol. 37:53-84.
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18
VI. APPENDICES
APPENDIX A
CONVERSION FACTORS
-------
CONVERSION FACTORS
Hectares x 2.471 = acres
Kilometers-x 0.62M = miles
Meters x 3.281 = feet -
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
Kilogra;i!s x 2.205 ~ pounds
Kilograms/square kilometer x 5.711 - Ibs/squaro mile
-------
APPENDIX B
TRIBUTARY FLOW DATA
-------
LAKE CODE 4013
TRIBUTARY FLOW INFORMATION FOR OKLAHOMA
TENKILLER FERRY RES.
TOTAL DRAINAGE AREA OF LAKEfSO KM) 4169.9
TRIbUTARY
4013AI
4013A2
4C13C1
4013ZZ
SUB-DRAINAGE
ARFAISQ KM)
4169.9
2483.8
795.1
891.0
NORMALIZED FLOWS (CM5)
JAN
35.40
IB. 69
6.46
6.80
FE8
45.31
30.58
11.69
11.61
MAR
41.06
34.55
11.81 '
15.36
APR
61.73
43.04
14.53
15.57
MAY
61.73
54.65
27.33
22.37
JUN
41.06
23.59
10. 5-*
9.34
JUL
47.57
15.43
7.02
6.23
AUG
29.45
11.69
2.52
3.96
SEH
20.67
7.50
1.47
2.44
OCT
18.41
11.52
2.04
3.68
NOV
28.60
17.70
3.54
5.66
uc.C
29.45
15.74
i.o3
S. 10
MEAN
38.32
23.68
8.45
9.04
SUMMARY
TOTAL DRAINAGE AREA OF LAKE =
SUM OF SUP-DRAINAGE AREAS =
4169.9
4169.9
TOTAL FLOW IN
TOTAL FLOW OUT
494.95
460.43
MEAN MONTHLY FLOWS AND DAILY FLOWS(CMS)
TRIBUTARY
4013A1
MONTH
YEAR
MEAN FLOW DAY
FLOW DAY
FLOW DAY
FLOW
4013A2
11
12
1
2
3
4
5
6
7
8
9
10
11
12
1
2
3
4
5
6
7
8
9
10
74
74
75
75
75
75
75
75
75
75
75
75
74
74
75
75
75
75
75
75
75
75
75
75
120.885
133.372
91.463
124.028
144.699
95.711
60.881
68.527
24.919
20.954
36.529
31.149
124.877
24.352
36.246
69.376
99.109
35.113
37.378
37.378
16.424
12.743
42.758
45.307
3
12
13
11
6
8
6
19
14
2
12
19
16
8
13
4
22
19
17
6
14
32.848
95.994
103.640
105.339 .
0.510
99.392 28
101.941 29
.••25.485
0.0
159.424
31.432
22.993
29.166
49.271
28.600 30
64.846 29
36.246
12.459
26.051
9.345
10.449
60.032
48.988
48.422
95. 145
-------
LAKE CODE 4013
TRIBUTARY FLO* INFORMATION KOR 0>\LArtO*A
TENKILLER FERRY PES.
03/25/77
MEAN MONTHLY FLOWS AND UAILY FLOWS
TRIBUTARY MONTH YEAR MEAN FLOW DAY
4013CI
4013ZZ
11
12
1
?
3
4
5
6
7
8
9
10
11
12
1
2
3
4
S
6
7
B
9
10
74
74
75
75
75
75
75
75
75
75
75
75
74
74
75
75
75
75
75
75
75
75
75
75
42.475
10.194
11.327
26.618
30.016
13.592
10.760
7.079
3.115
2.095
4.531
4.814
37.945
9.061
10.194
23.5C3
26.618
12.176
9.6?8
6.230
2.832
1.98?
1.416
4.248
3
10
19
16
13
13
5
22
19
29
7
14
FLOW DAf
FLO* DAY
FLOW
231.349
14.442
7.929
9.061
37.661
10.222
19.539
8.778
2.265
1.841
1.416
30
23
16.820
8.495
30
7.079
-------
APPENDIX C
PHYSICAL AND CHEMICAL DATA
-------
S70RET SETRfEVAC DATE 77/03/28
/TYPA/AMBNT/LAKE
DATE
FROM
TO
74/04/03
74/06/14
74/08/30
74/10/21
TIME
OF
DAY
10
10
10
10
10
10
12
12
12
12
12
12
12
12
09
09
09
09
09
09
09
09
09
11
11
1
1
1
1
1
1
1
10
10
10
10
10
10
25
25
25
25
25
25
25
25
45
45
45
45
45
45
45
45
45
35
35
35
35
35
35
35
35
35
OEPTri
FEET
0000
0005
0015
0050
0100
0140
0000
0005
0020
0040
0070
0090
0115
0146
0000
0015
0030
0035
0045
0055
0080
0100
0125
0000
0005
0015
0035
0055
0075
0095
0115
0136
00010
WATER
TEMP
CENT
11.4
11.2
11.0
10.3
8.8
e.o
25.3
24.3
23.4
22.1
20.1
18.2
15.2
13.5
27.0
27.0
27.0
26.6
26.1
25.3
21.1
19.9
18.2
19.6
19.6
19.6
19.6
19.6
19.6
19.6
19.3
18.4
401301
35 35 50.0 095 02 20.0 4
TENKILLE* FER^Y *ESEHVOIR
40135 OKLAHOMA
100991
11EPALES
0^001002
0145 FEET DEPTH CLASS
003CO
DO
MG/L
10.4
9.6
9.8
9.4
9.0
8.0
6.8
4.8
4.4
4.0
3.6
1.0
7.0
6.8
4.6
3.2
1,2
0.1
0.2
0.2
0.0
6.2
5.8
6.0
6.0
6.8
5.8
7.4
7.4
0.4
00077 00094
TRANSP CNDUCTVY
SECCHI FIELD
INCHES MICROMHO
36 118
119
116
115
110
104
132 175
168
167
158
123
148
140
137
96 142
152
153
152
153
160
110
105
125
62 145
145
145
145
145
144
143
153
189
00400
PH
SU
7.60
7.60
7.60
7.50
7.30
7.10
8.90
6.40
7.90
7.90
7.40
7.40
7.50
7.40
8.30
8.30
8.00
7.90
7.45
7.70
7.60
7.50
7.30
7.22
7.21
7.21
7.23
7.23
7.23
7.17
6.93
6.87
00410
T ALK
CAC03
MG/L
60
53
54
54
64
65
86
98
74
58
74
74
80
75
74
75
74
77
83
65
66
78
74
74
75
74
74
74
75
79
91
00610
NH3-N
TOTAL
MG/L
0.040
0.030
0.030
0.030
0.050
0.070
0.050
0.050
0.050
0.050
0.030
0.030
0.060
0.050
0.040
0.050
0.040
0.050
0.050
0.090
0.380
1.260
0.020
0.020
0.020K
0.020K
0.020K
0.020K
0.020K
0.040
0.920
00
00625
TOT KJEL
N
MG/L
0.300
0.200K
0.200K
0.200K
0.200
0.500
0.600
0.300
0.300
0.200
0.300
0.200
0.200
0.500
1.200
0.400
0.200
0.200K
0.200
0.200
0.200
0.600
1.400
0.600
0.200K
0.200K
0.200K
0.200
0.200
0.300
0.500
1.200
00630
N02«>N03
N-TOTAL
MG/L
0.800
0.810
0.820
0.820
0.840
0.840
0.510
0.540
0.650
0.650
0.780
O.B60
0.880
0.100
0.100
0.170
0.180
0.180
0.140
0.450
0.200
0.060
0.350
0.350
0.340
0.340
0.340
0.330
0.350
0.490
0.220
00b71
PHQb-jI^
OWTnO
MG/L t3
0.040
0.04d
0.044
•0.042
0.051
0.050
0.011
0.011
0.014
0.04J
0.012
0.014
O.Olb
0.023
0.015
0.010
0.010
0.016
0.014
0.025
0.038
0.054
0.005
O.OOfc
O.OOb
O.OOb
0.006
O.OOfi
" 0.00 /
0.012
0.019
K V<\LUE KNOWN TO bi-
LESS THAN INDICATED
-------
STORF.T RETRIEVAL DATE 77/0 V2ft
/TrDA/AMBNT/LAKE
401301
35 35 50.0 095 02 20.0 4
TtNKILLER FERRY RESERVOIR
40135 OKLAHOMA
100991
UEPALES 04001002
0145 FEET DEPTH CLASS 00
00665 32217 00031
DATE
FROM
ro
74/04/03
74/06/14
74/08/30
74/10/21
TIME
OF
UAY
10
10
10
10
10
10
12
12
12
12
12
12
12
12
09
09
09
09
09
09
09
09
09
11
11
11
11
11
11
11
11
11
11
11
10
10
10
10
10
10
25
25
25
25
25
?5
25
25
45
45
45
45
45
45
45
45
45
35
35
35
35
35
35
35
35
35
35
35
DEPTH
FEET
0000
0005
0015
0050
0100
0140
0000
0005
0020
0040
0070
0090
0115
0146
0000
0015
0030
0035
0045
0055
0080
0100
0125
0000
0001
0005
0011
0015
0035
0055
0075
0095
0115
0136
PHOS-TOT OLRPHYL INCOT LT
MG/L
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
u.
0.
0.
0.
0.
0.
0.
0.
0.
0.
V •
0.
0.
0.
0.
0.
0.
0.
0.
A REMNING
P UG/L PERCENT
048 2.9
047
045
045
076
199
023 0.1
020
022
023
080
022
021
232
035 6.6
030
025
023
031
027
063
15<.
347
052 6.1
50.0
031
1.0
031
030
032
030
034
096
113
-------
ST03ET •••ETR1EVAL DATE 77/03/28
/TYPA/AV-BNT/LAKF
DATE
FROM
TO
74/04/03
74/06/12
74/08/30
74/10/21
TIME DEPTH
OF
DAY FEET
10 45 0000
10 45 0005
10 45 0015
10 45 0040
10 45 0080
10 45 0110
13 00 0000
13 00 0005
13 00 0010
13 00 0020
13 00 0035
13 00 0045
13 00 0070
13 00 0090
13 00 0100
13 00 0121
10 4C 0000
10 40 0015
10 40 0030
10 40 0035
10 40 0045
10 40 0060
10 40 0085
10 40 0100
10 50 0000
10 50 0005
10 SO 0015
10 50 0035
10 50 0055
10 50 0075
10 50 0096
00010
4ATER
TEMP
CENT
12.0
12.0
11.9
11.5
9.8
9.0
25.6
25.5
24.4
23.7
22.5
21.1
20.2
18.3
16.1
14.8
27.1
"27.1
26.9
26.6
26.3
23.3
20.5
19.8
19.5
19.5
19.5
19.5
19.5
19.5
19.2
401302
35 38 45.0 095 00 10.0 4
TtNKlLLER FERRY RESERVOIR
40021 OKLAHOMA
100991
11EPALES
04001002
0115 FEET DEPTH CLASS
00300
DO
MG/L
10.2
10.0
10.0
9.0
8.6
9.4
9.2
7.6
4.8
5.2
5.0
2.0
2.2
0.8
6.6
6.4
4.2
2.4
1.6
0.2
0.4
0.8
7.2
7.4
7.6
5.8
7.4
7.2
4.0
00077 00094
TRANSP CNDUCTVY
SECCHI FIELD
INCHES MICROMHO
42 125
125
126
127
123
115
115 17b
171
169
168
151
121
81
152
147
148
96 155
155
156
156
150
156
119
144
62 145
145
145
143
145
143
155
00400
PH
SU
7.60
7.80
7.70
7.60
7.40
7.20
8.90
9.00
8.80
8.50
7.80
7.50
7.40
7.50
7.50
7.20
8.20
8.20
7.90
7.80
7.70
7.60
7.50
7.40
7.55
7.55
7.55
7.53
7.49
7.47
6.99
00410
T ALK
CAC03
MG/L
74
77
79
80
81
75
83
80
78
82
73
57
41
79
87
90
76
75
78
77
78
84
71
85
71
71
70
74
77
77
80
00610
NH3-N
TOTAL
MG/L
0.030
0.020
0.020
0.020
0.030
0.040
0.030
0.040
0.040
0.060
0.040
0.080
U.150
0.100
0.090
0.040
0.060
0.040
0.060
0.080
0.150
0.120
0.320
0.750
0.040
0.020
0.020K
0.020
0.020K
0.020
0.020K
00
00625
TOT KJEL
N
MG/L
0.300
0.200K
0.200K
0.200K
0.200K
0.200
0.400
0.400
0.400
0.400
0.300
0.400
0.600
0.300
0.300
0.300
0.500
0.200
0.200
0.200K
0.200K
0.200K
0.500
0.900
0.400
0.200
0.200K
0.200
0.200
0.200
0.200
00630
N02&N03
N-TOTAL
MG/L
0.810
0.820
0.820
0.840
0.880
0.900
0.520
0.420
0.470
0.500
0.650
0.660
0.580
0.860
0.890
0.880
0.070
0.050
0.080
0.120
0.130
0.160
0.230
0.050
0.250
0.240
0.250
0.240
0.240
0.250
0.480
00671
PHOS-UIS
OR1 riU
MG/L P
U.038
u.039
0.038
0.039
0.043
0.047
0.004
0.010
0.006
0.003
u.Olfa
0.056
0.077
0.022
0.021
0.028
0.008
0.012
0.011
0.014
0.011
0.014
0.02o
O.OJ2
0.005
0.00-4
0.003
0.003
0.003
U.003
0.005
* V/-L.UE
-------
S703ET RETRIEVAL CAJE 77/03/(2S
/TYPA/AM6NT/LAKE
401302
35 38 45.0 095 00 10.0 4
TENKILLER FERRY RESERVOIR
40021 OKLAHOMA
100991
11EPALES
0115 FEET
04001002
DEPTH CLASS 00
DATE
FROM
TO
74/04/03
74/06/12
74/08/30
74/10/21
00665 32217 00031
TIME DEPTH PHOS-TOT CriLRPHYL INCDT LT
OF A REMNING
DAY FEET
10
10
10
10
10
10
1.3
13
13
13
13
13
13
13
13
13
10
10
10
10
10
10
10
10
10
10
10
10
10
10
10
10
10
10
1C
45
45
45
45
45
45
00
00
00
CO
00
00
00
00
00
00
40
40
40
40
40
40
40
40
40
40
50
50
50
50
50
50
50
50
50
0000
0005
0015
0040
0080
0110
0000
0005
0010
0020
0035
0045
0070
0090
0100
0121
0000
0015
0016
0021
0030
0035
0045
0060
0085
0100
0000
0001
0005
0013
0015
0035
0055
0075
0096
MG/L P
0,
0.
0.
0.
0,
0.
0,
0.
0,
0,
c.
0.
0,
0.
0,
0.
0,
c,
0,
0.
0,
0.
0,
0,
o,
c,
c,
0,
0.
0.
0,
.039
.042
.040
.039
,041
,080
.029
.025
.025
.025
.038
, 1 Itt
.162
.058
.043
.049
.030
.030
.026
.030
.026
.032
,107
.186
.023
.020
.019
.021
.038
.030
.15*
UG/L PERCENT
4.9
0.2 . . .
5.7
5.0
1.0
7.1
50.0
1.0
-------
STORET RF.TniEVAL DATE 77/Q3/2B
/TYPA/AM8NT/LAKE
DATE
FROM
TO
7<«/04/03
74/06/14
74/06/30
74/10/21
00010
TIME DEPTH WATER
OF TEMP
DAY FEET
11
11
11
11
11
10
10
10
10
10
10
i
i
i
i
i
10
10
10
10
10
10
io
30
30
30
30
30
55
55
55
55
55
55
15
15
15
15
15
15
15
15
15
15
15
15
0000
0005
0015
0040
0080
0000
0005
0015
0030
0045
0036
0000
0025
0035
0050
0065
0000
0005
0015
0025
0045
0065
00d3
CENT
12
12
12
12
10
25
25
25
23
20
20
27
27
26
25
22
19
19
19
19
19
19
19
.7
.7
.6
.1
.1
.8
.7
.1
.1
.6
.1
.4
.3
.6
'.5
.5
.5
.5
.5
.5
.5
.2
. 1
00300
DO .
MG/L
10.
10.
9.
9.
10.
9.
5.
5.
4.
6.
5.
0.
0.
0.
B.
7.
7.
7.
7.
6.
4.
0
2
e
0
0
2
4
4
8
4
0
5
0
0
0
8
8
6
6
2
2
401303
35 41 35.0 094 57 40.0 4
TENKILLER FERRY RESERVOIR
40021 OKLAHOMA
100991
11EPALES
04001002
0090 FEET DEPTH CLASS
00300
DO
MG/L
10.0
10.2
9.8
9.0
10.0
9.2
5.4
5.4
4.8
6.4
5.0
0.5
0.0
0.0
B.O
7.8
7.8
7.6
7.6
6.2
4.2
00077 00094
TRANSP CNDUCTVY
SECCHI FIELD
INCHES MICROMHO
48 132
132
133
131
132
80 179
177
175
164
166
143
72 157
159
166
177
179
58 145
145
145
143
145
151
155
00400
PH
SU
7.80
7.80
7.80
7.70
7.30
8.90
8.90
8.80
7.90
7.30
7.30
8.26
7.9o
7.60
7.50
7.40
7.76
7.7b
7.75
7.73
7.71
7.37
7.19
00410
T ALK
CAC03
MG/L
75
73
72
72
70
78
76
78
77
44
40
76
76
79
90
91
75
74
74
74
73
77
81
00610
NH3-N
TOTAL
MG/L
0.030
0.030
0.030
0.040
0.050
0.070
0.040
0.060
0.070
0.090
0.130
0.060
0.060
0.120
0.410
0.730
0.040
0.030
0.030
0.030
0.050
0.130
0.250
00
00625
TOT KJEL
N
MG/L
0.400
0.200
0.200
0.200
0.300
0.400
0.300
0.300
0.300
0.500
0.500
0.400
0.200
0.300
0,500
0.900
0.600
0.200
0,200
0.200K
0.200
0.300
0.600
00630
N02&N03
N-TOTAL
MG/L
0.820
0.810
0.840
0.870
1.080
0.570
0.500
0.500
0.620
0.580
0.550
0.040
0.040
0.070
0.020
0.040
0.240
0.220
0.220
0.220
0.220
0.220
0.240
00071
PHOS-DIS
ORTrlO
MG/L P
0.034
0.034
0.026
0.028
0.036
0.012
0.009
0.009
0.014
0.089
0.0 «4
0.011
0.012
0.016
0.026
0.032
0.004
0.003
0.003
0.004
0.004
0.007
0.018
K VALUt Ki'iOWM TO be
LESS THAN INDICATED
-------
STORE! RETRIEVAL GATE 77/03/28
4C1303
35 41 25.0 094 57 40.0 4
TENKILLER FERRY RESERVOIR
40021 OKLAHOMA
100991
/TYPA/AMBNT/LAKE:
11EPALES
0090 FEET
04001002
DEPTH CLASS 00
DATE
FROM
TO
74/04/03
74/06/14
74/08/30
74/10/21
00665 32217 00031
TIME DEPTH PHOS-TUT CHLRPHYL INCOT LT
OF A REMNING
DAY FEET
11
11
11
11
11
10
10
10
10
10
10
10
11
11
11
11
11
10
10
10
10
10
10
10
10
30
30
30
30
30
55
55
55
55
55
55
55
15
15
15
15
15
15
15
15
15
15
15
15
15
0000
0005
0015
0040
0080
0000
0005
0015
0019
0030
0045
0066
0000
0025
0035
0050
0065
0000
0005
0012
0015
0025
0045
0065
0083
MG/L u UG/L PERCENT
0.
0.
0,
0.
0.
0.
0,
0,
3,
0,
0,
0,
0,
0,
0.
0,
0.
0.
0.
0,
0,
0,
0,
.041 7.1
,039
.038
.042
.055
.031 0.3
.028
.025
l.C
.033
.172
.161
.038 6.6
.034
.039
>08<«
.130
.024 14.4
.021
1.0
.020
,021
.021
.043
.OM5
-------
STOKE! RETRIEVAL O.'JF. 77/03/28
/TYPA/AMBNT/LAKE
DATE
FROM
TO
74/04/03
74/06/14
74/08/30
74/10/21
TIME
OF
DAY
12
12
12
12
10
10
10
10
10
10
11
11
11
11
09
09
09
09
00
00
00
00
30
30
30
30
30
30
45
45
45
45
45
45
45
45
DEPTH
FEET
0000
0005
0015
0038
0000
0005
0010
0015
0025
0050
0000
0015
0025
0028
0000
0005
0020
0034
00010
WATER
TEMP
CENT
15.3
15.3
15.3
13.6
25.6
25.6
23.3
22.1
20.5
20.4
?7.1
27.0
26.7
26.3
18.6
18.5
IB. 2
17.2
401304
35 45 45.0 094 53 50.0 4
TENKILLER FERRY RESERVOIR
400,21 OKLAHOMA
100992
11EPALES
04001002
0043 FEET DEPTH CLASS
00300
DO
MG/L
9.0
9.4
8.8
10.8
7.6
6.2
5.6
5.2
5.2
5.0
3.4
3.2
10.0
10.0
9.4
7.4
00077
TRANSP
SECCHI
INCHES
30
29
26
48
00094
CNDUCTVY
FIELD
MICROMHO
154
153
154
150
169
168
139
116
120
119
183
184
196
201
147
147
150
167
00400
PH
SU
7.75
7.75
7.65
7.50
8.90
9.00
9.10
7.80
7.50
7.40
7.80
7.75
7.70
7.60
8.51
8.51
8.43
7.39
00410
T ALK
CAC03
MG/L
73
75
77
83
72
75
55
56
82
82
86
92
79
80
81
91
00610
NH3-N
TOTAL
MG/L
0.040
0.040
0.040
0.070
0.050
0.040
0.080
0.100
0.190
0.190
0.270
0.300
0.030
0.020K
0.040
0.100
00
00625
TOT KJEL
N
MG/L
0.600
0.300
0.300
0.300
0.500
0.500
0.400
0.400
0.300
0.400
0.900
0.600
0.700
0.600
0.600
0.300
0.400
0.200
00630
N02&N03
N-TOTAL
MG/L
0.920
0.920
0.920
0.890
0.480
0.430
0.840
0.850
0.210
0.170
0.290
0.180
0.220
0.200
0.280
0.550
00671
PHOS-LJIS
ORTHO
MG/L P
0.038
0.034
0.033
0.036
0.014
0.017
0.084
0.085
0.029
0.027
0.031
0.026
0.007
0.003
0.008
0.019
K VALUE M-iOWN TO 8!i
LESS THAN INDICATED
-------
STORET RETRIEVAL OAFE 77/03/28.
401304
35 45 45.0 094 53 50.0 4
TENKILLER FERRY RESERVOIR
40021 OKLAHOMA
100992
/TYPA/AMBNT/LAKE
11EPALES
0043 FEET
04001002
DEPTH CLASS 00
DATE
FROM
TO
74/04/03
74/06/14
74/08/30
74/10/21
00665 32217 00031
TIME DEPTH PHOS-TOT CHLRPHYL INCDT LT
OF A REMNING
DAY FEET
12
12
12
12
10
10
10
10
10
10
10
11
11
11
11
09
09
09
09
09
00
00
00
00
30
30
30
30
30
30
30
45
45
45
45
45
45
45
45
45
0000
0005
0015
0038
0000
0001
0005
0010
0015
0025
0050
0000
0015
0025
0028
0000
0005
0009
0020
0034
MG/L P UG/L PERCENT
0.
0.
0,
0.
0.
0.
0,
0.
0.
0,
0.
0.
0,
C,
0.
0,
0.
0,
.051 7.0
.047
.049
.061
,035 0.7
50.0
.040
.035
.118
.118
.143
,067 12.0
.093
.141
.141
.044 24.6
.026
1.0
.046
,114
-------
APPENDIX D
TRIBUTARY AND WASTEWATER
TREATMENT PLANT DATA
-------
RETRIEVAL DATE 77/03/24
/TYPA/AMBNT/STRf.AM
DATE TIME DEPTH N02NN03
FRO* OF
TO DAY FEET
74/1 1/03
74/12/12
75/01/13
75/02/11
75/03/06
75/04/OH
75/04/28
75/05/08
75/05/29
75/10/14
10 on
18 30
18 15
06 15
13 50
19 00
11 00
10 40
14 10
4013A1
35 35 50.0 095 02 15.0 4
ILLINOIS RIVER
40 15 WEflSEKS FALLS
0/TENKILLER FERRY RES 1009*1
OUTLET OF TENKILLER RES JAM ON HWY 100
11EPALES 04001004
0000 FEET DEPTH CLASS 00
063C
NN03
OTAL
G/L
0.36S
0.490
C.520
0.520
0.550
0.650
0.030
0,960
0.960
U.430
00625
TOT KJEL
N
MG/L
0.300
1.100
1.200
0.900
1.400
2.000
1.100
1.800
0.350
2.000
OC610
NH3-N
TOTAL
MG/L
0.030
0.020
0.016
C.016
0.048
C.015
0.030
0.025
0.010
0.145
00671
PhOS-uIS
ORTrtO
MG/L P
0.030
0.030
0.025
0.016
0.016
0.040
0.005K
0.045
0.055
0.030
00665
PHOS-TOT
MG/L P
0.070
0.050
0.070
0.020
0.040
O.Q55
0.020
0.050
0.060
0.090
K VALUE KNOWN TO BE
LESS TlAN
-------
STOKET RETRIEVAL GATE 77/03/2**
/TfPA/AMBNT/STREAM
4IM3A2
35 55 25.0 094 56 00.0 <*
ILLINOIS HIVE*
<«0 7.5 WELLING Nrf
T/TENKILLER FERRY RES 100992
HrfY 62 BROG 2.2 MI NE OF TAHLEOUAH
11EPALES 04001004
0000 FEET DEPTH CLASS 00
DATE
TO
74/11/02
74/12/12
75/01/19
75/02/16
75/03/08
75/04/13
75/04/30
75/05/04
75/05/29
75/06/22
75/07/19
75/08/17
75/09/06
75/10/14
00630 00625
TIMF DEPTri N02».N03 TOT KJEL
OF N-TOTAL N
DAY FEET Mb/L
12
14
13
14
14
17
16
16
16
10
09
08
09
09
30 0.720
30 1.280
45
00
30
00
30
00
.340
.300
.585
.400
.100
.100
30 0.575
00 0.870
35 0.260
30 0.640
00 U.380
10 1.150
MG/L
1.
1.
2.
1.
1.
1.
0.
0.
1.
1.
0.
0.
1.
1.
300
300
500
400
900
800
675
250
700
050
250
600
200
600
0,^610 00671 00665
NH3-N PnOb-OlS PHOS-TOT
TOTAL ORTHO
MG/L
0.
0.
0.
0.
0.
0.
!>.
0.
C.
C.
0.
o.
0.
c.
035
025
032
024
072
035
025
007
030
025
010
020
020
035
MG/L
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
p
070
040
045
040
04b
035
040
060
075
065
035
075
055
045
MG/L P
0
0
0
0
0
0
0
0
0
0
0
0
0
c
.135
.070
.050
.040
.070
.040
.090
.080
.220
.085
.090
.125
.110
.080
-------
STOr?ET
DATE 7f/'j3/24
35 36 35.0 095 01 00.0 4
PINE BRANCH CREEK
40 15 WEriBERS FALLS
T/TENKILLER FERRY RES 100991
ttRDG ON DIHT RO 1 MI NE OF RES
11EPALES 04001004
0000 FEET DEPTH CLASS 00
DATE
FROM
TO
74/11/03
74/12/10
75/01/13
75/02/11
75/03/06
75/04/OH
75/04/28
75/05/16
75/05/2^
TI"E UtP^
OF
DAf FEET
10 30
18 30
06 30
18 30
14 10
18 45
11 15
11 19
00630
N02«.N03
N-TOTAL
MG/L
0.056
0.50*
0.016
0.015
0.012
0.015
0.6*0
0.060
0.015
00625
TOT KJEL
N
MG/L
0.200
1.000
.2.000
0.700
1.150
1.^00
1.650
0.310
C.150
00610
Nn3-N
TOTAL
MG/L
0.020
0.030
0.032
0.016
0.024
0.025
0.025
0.075
0.005
00671
PHOS-DIS
ORTHO
MG/L P
0.010
0.030
0.010
0.008K
0.008K
0.010
0.070
0.005
0.005K
00665
PHOS-TOT
MG/L P
0.020
0.050
0.010
0.010K
0.010K
0.030
0.130
0.010*
0.010K
K VALUE KNOWN TO BE
LESS THAN INDICATED
-------
STO^LT
OATE. 77/03/24
4013d
35 55 25.C 09*. 50
BArWOrt F03K
<»0 7.5 WELLING ME
T/TENMLLt* FE«RY RES
H«IY 51 6RDG 0.4 MI
11EPALES
0000 FEET OEPTrt
15.0 4
1009*2
SE ELOON JCT W HWr 62
04001004
CLASS 00
DATC TIMf; DEPTH H02&N03
FROM OF
TO DAY FEET
12 SS
14 30
14 SO
11 ?0
16 50
17 35
15 30
22 00
10 00
09 40
09 SO
07 50
10 15
13 35
74/12/10
75/02/16
75/03/13
75/04/13
75/0<«/30
75/05/05
75/05/23
75/05/30
75/06/22
75/07/19
75/08/29
75/09/07
75/10/04
0630
:&N03
OTAL
IG/L
0.576
0.740
0.687
0.690
0.590
0.590
C.510
0.500
0.490
0.4dO
C.315
C.280
U.260
C.400
00625
TOT KJEL
N
MG/L
1.400
0.700
1.200
1.900
2.200
2.000
0.150
0.100
0.100
1.950
1.700
0.450
0.500
1.300
00610
NH3-N
TOTAL
MG/L
0.020
0.015
G.016
0.072
0.030
0.025
0.005K
0.010
0.005
0.090
0.035
0.025
0.020
0.030
00671
PhOb-OIS
ORTHO
MG/L P
0.060
0.015
0.015
0.032
0.015
0.025
0.030
0.020
C.015
0.015
0.015
0.015
0.040
0.015
00665
PHOS-TUT
MG/L P
0.030
0.015
0.080
0.015
0.050
0.030
0.030
0.020
0.040
0.060
0.040
0.020
K VALUE KNOWN TO Bt
LESS THAN INDICATED
-------
bTORET RETRIEVAL DATE 77/03/24
4013XA AS4013XA P010500
35 54 00.0 094 5H 30.0 4
TAHLEUUAH
<»0 CHEROKEE CO MAP
T/TENKILLER FERRY RESER. 1009*2
BRANCH -CREEK
11EPALES 00001004
0000 FEET DEPTH CLASS 00
DATE
FPOM
ro
75/06/13
CP(T)-
75/06/13
75/07/09
CP-
75/07/08
75/07/31
75/08/21
CP(T) -
75/08/21
75/09/24
75/10/15
75/11/10
CP(T>-
75/11/10
75/12/02
CP-
75/12/03
76/01/05
CPU>-
76/01/06
7fr/02/19
CP-
76/02/20
00630
TIME DEPTH N02«.NOJ
OF N-TOTAL
DAY FEET MG/L
00
24
00
24
21
24
00
00
24
12
12
12
12
30
UO
00
00
00
00
00
00
00
00
00
on
00
00
00
00
00
7
10
15
15
4
15
13
2
4
V
.7uO
.500
.000
.400
.700
.400
.800
.880
.100
.525
00625
TOT KJEL
N
MG/L
3.8CO
1.900
2.100
2.200
5.100
3.300
2.700
11.000
3.700
9.SOO
00610 00671 00665 50051 50053
NH3-N PnOS-OIS PriOS-TOT FLOW CGNouIT
TOTAL ORTHO RATE FLOw-MGO
MG/L MG/L P MG/L P INST MGO MONTHLY
0
0
0
0
0
n
0
1
0
1
.150
.180
.050
.110
.125
.325
.042
.650
.110
.200
4.400
6.400
10.000
6.300
9.700
7.700
4.500
4.700
2.750
4.500
6.450
10.000
4.900
6.700
10.000
8.100
7.100
5.100
3.200
1.440
0.901
0.840
0.900
0.925
0.814
0.849
1.170
0.898
0.749
1.600
0.958
0.861
0.820
1.030
0.844
0.796
0.970
1.100
0.739
-------
APPENDIX E
PARAMETRIC RANKINGS OF LAKES
SAMPLED BY NES IN 1974
STATE OF OKLAHOMA
-------
OAT4 TO r'F. USEf I-
ALT'JS
LAKE
a o 0 ^
'.DOS
4006
4007
400b
400'^
4010
4011
4012
40 in
an 1 <»
4 (i 15
4«34
FilPT
FOSS Dfl"
LAKF
THt
LAKE
KEYSTONE PtsP
OOLOGAri LAf.t
TF.NKILLEP FE
T E x o v ft LA .
«£•-.! 4\
'J.1-1
0.020
'i . n j 7
o.^l
G • 0 J H
0.070
0.027
0.142
0 . 0 o 7
0.057
0.136
O.nb*
0.039
O.n?7
0.080
O.nt?
"E HI AM
0.060
0.07 o
0.070
0 .4 OS
0.110
o.n*
0.090
1.780
0.740
0.250
0.690
0.580
0.550
0.150
0.230
0.160
MfA°\tC
468.6
-------
PE&CEMT OF LAKES *ITH HIGHER VALUES (NUMBFR OF LAivES WITH HIGHER VALUES)
CODE LAKE NA*>E
40oi ALTUS RFSERVMR
4002 AQBUCKLE LAr\i-
4003 LAKE ELLSWORTH
4004 LAKE EUFAIJLA
4005 FORT COPB RESERVOIR
4006 FORT SUPPLY RESERVOIR
4007 FOSS DAM RESERVOIR
4008 LAKE FRANCES
4009 GRANfJ LAKE O1 THE CriE^OK
4010 LAKE HEFNER
4011 KEYSTONE WEScRVOI'J
4012 OOLOGAH LAKt
4013 TENKILLER FERRY RESERVOI
4014 LAKE
4015 WISTER
4S34 TEXOMA LAKE
MEni AN
TOTAL P
60 (
100 (
80 (
20 (
73 (
33 (
93 (
0 (
13 (
47 (
7 (
40 (
67 (
87 (
27 (
53 (
•3)
15)
12)
3)
1 1)
5)
14)
0)
2)
7)
1)
6)
10)
13)
4)
8)
MEDIAN
INORG N
100
90
90
33
73
67
80
0
7
40
13
20
27
60
47
53
( 15)
( 13)
( 13)
( 5)
( 11)
( 10)
( 12)
( 0)
( 1)
( 6)
( 2)
( 3)
( 4)
( 9)
( 7i
( 8)
500-
MEAN SEC
47
93
80
27
87
0
60
7
40
67
13
20
ion
53
33
73
( 7)
( 14)
( 12)
( 4)
( 13)
( 0)
( 9)
( 1)
( 6)
( 10)
( 2)
( 3)
( 15)
( fi)
( 5)
( 11)
^EAN
CHLCMA
13
53
33
100
7
27
67
47
60
73
0
80
67
40
93
20
( 2)
( 8)
( 5)
( 15)
( 1)
( 4)
( 13)
( 7)
( 9)
( 11)
( 0)
( 12)
( 10)
( 6)
( 14)
( 3)
15-
MIN 00
80 (
33 (
60 (
47 (
80 (
100 (
80 (
93 (
20 (
67 (
13 (
33 (
3 (
53 (
3 (
33 (
11)
4)
9)
7)
11)
15)
11)
14)
3)
10)
2)
4)
0)
8)
0)
4)
MEDIAN
DISS ORTHO P
73
93
87
33
67
60
100
7
13
20
0
27
50
80
40
50
( 11)
( 14)
( 13)
( S)
( 10)
( 9)
( 1^)
( 1)
( ?)
( 3)
( 0)
( 4)
( 7)
( 1?)
( M
( 7)
------- |