U.S. ENVIRONMENTAL PROTECTION AGENCY
NATIONAL EUTROPHICATION SURVEY
WORKING PAPER SERIES
REPORT
ON
STOCKTON RESERVOIR
BADE, POLK, AND CEDAR COUNTIES
MISSOURI
EPA REGION VII
WORKING PAPER No, 549
CORVALLIS ENVIRONMENTAL RESEARCH LABORATORY - CORVALLIS, OREGON
and
ENVIRONMENTAL MONITORING & SUPPORT LABORATORY - LAS VEGAS, NEVADA
•&G.P.O. 699-440
-------
REPORT
ON
STOCKTON RESERVOIR
DADE, POLK, AND CEDAR COUNTIES
MISSOURI
EPA REGION VII
WORKING PAPER No, 549
V/ITH THE COOPERATION OF THE
MISSOURI DEPARTMENT OF NATURAL RESOURCES
AND THE
MISSOURI NATIONAL GUARD
FEBRUARY, 1977
-------
REPORT ON STOCKTON RESERVOIR
DADE, POLK, AND CEDAR COUNTIES, MISSOURI
EPA REGION VII
by
National Eutrophication Survey
Water and Land Monitoring Branch
Monitoring Applications Laboratory
Environmental Monitoring & Support Laboratory
Las Vegas, Nevada
and
Eutrophication Survey Branch
Corvallis Environmental Research Laboratory
Corvallis, Oregon
Working Paper No. 549
OFFICE OF RESEARCH AND DEVELOPMENT
U.S. ENVIRONMENTAL PROTECTION AGENCY
February, 1977
-------
CONTENTS
Page
Foreword ii
List of Missouri 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 6
IV. Nutrient Loadings 12
V. Literature Reviewed 19
VI. Appendices 20
-------
11
FOREWORD
The National Eutroph1cat1on Survey was Initiated 1n 1972 1n
response to an Administration commitment to Investigate the nation-
wide threat of accelerated eutrophlcatlon 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 nonpolnt source pollution abatement 1n lake water-
sheds.
ANALYTIC APPROACH
The mathematical and statistical procedures selected for the
Survey's eutrophlcatlon 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 eutrophlcatlon 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 1s documented. The report 1s formatted to provide state
environmental agencies with specific Information for basin
E Tanning [§303(e)], water quality criteria/standards review
§303(c)], clean lakes [§314(a,bJ], and water quality monitoring
[§106 and §305(b)] activities mandated by the Federal Water
Pollution Control Act Amendments of 1972.
-------
111
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 Missouri Department of Natural
Resources for professional involvement, to the Missouri National
Guard for conducting the tributary sampling phase of the Survey,
and to those Missouri wastewater treatment plant operators who
provided effluent samples and flow data.
The staff of the Missouri Department of Natural Resources,
James Wilson, Director; the Division of Environmental Quality,
Ken Karch, Director; and the Water Quality Program, James Odendahl,
Director, provided invaluable lake documentation and counsel during
the Survey, reviewed the preliminary reports and provided critiques
most useful in the preparation of this Working Paper series.
Major General Charles M. Kiefner, the Adjutant General of Missouri,
and Project Officer Captain Donald L. Well en, who directed the
volunteer efforts of the Missouri National Guardsmen, are also
gratefully acknowledged for their assistance to the Survey.
-------
IV
LAKE NAME
NATIONAL EUTROPHICATION SURVEY
STUDY LAKES
STATE OF MISSOURI
Clearwater Lake
Pomme de Terre Reservoir
Stockton Reservoir
Lake Taneycomo
Thomas Hill Reservoir
Lake Wappapello
COUNTY
Reynolds
Polk, Hickory
Dade, Polk, Cedar
Taney
Macon, Randolph
Wayne, Butler
-------
STOCKTON RESERVOIR
Tributary Sampling Site
X Lake Sampling Site
Sewage Treatment Facility
13 Drainage Area Boundary
III Land Subject to Inundation
ip 20 so Km
STOCKTON
RESERVOIR
Springfield
Map Location
-------
REPORT ON STOCKTON RESERVOIR, MISSOURI
STORET NO. 2903
I. CONCLUSIONS
A. Trophic Condition:*
Based upon field observations and Survey data, Stockton
Reservoir is considered early eutrophic. Chlorophyll a_ values
ranged from a low of 1.3 yg/1 in the summer to a high of 29.2
yg/1 in the spring with a mean of 9.0 yg/1. Low Secchi disc
visibility (mean of 180 cm) and low potential for primary
productivity as measured by algal assay control yield were
reported. There were oxygen depletion and hydrogen sulfide
production noted at Stations 03 and 04 during the summer sam-
pling season and at Station 04 during the fall. Of the six
Missouri lakes sampled in 1974, four had greater median total
phosphorus levels, one had greater median inorganic nitrogen
values, and three had greater median dissolved orthophosphorus
levels than Stockton Reservoir. It should be noted that although
phosphorus levels in the lake were similar throughout the seasons,
the spring chlorophyll a^ values observed were an order of
magnitude higher than summer values and approximately 4-5 times
those observed in the fall. This same spring phenomenon can be
observed in the algal counts for the similar centric diatom-based
communities found in the lake all three sampling dates.
*See Appendix E.
-------
Survey limnologists reported no problem conditions in the
lake during the sampling year.
B. Rate-Limiting Nutrient:
Algal assay results indicate that Stockton Reservoir was
limited by available phosphorus levels. Spikes with phosphorus
or nitrogen and phosphorus simultaneously resulted in increased
assay yields. Addition of nitrogen alone did not stimulate a
growth response. The ratios of available nitrogen to orthophos-
phorus (N/P) in sampled waters substantiate phosphorus limitation.
C. Nutrient Controllability:
1. Point sources -
Point sources were estimated to contribute 42.0% of the
total phosphorus load to Stockton Reservoir during the sam-
pling year. The Springfield Northwest wastewater treatment
plant contributed 25.6% of the total load and the city of
Ash Grove contributed 7.7%. The remaining 12 plants were
estimated to contribute 8.7% of the phosphorus load. There
are a number of small private,facilities and four industrial
plants (Kerr-McGee Chemical Corporation; Conco Quarries, Inc.;
Greismer Stone Company; Advanced Circuiting - a Division of
Litton Inc.) which are not included in the nutrient budgets
for Stockton Reservoir (Missouri Department of Natural Resources,
manuscript). It is not known at this time how much these un-
measured sources contributed to nutrient loadings in the
reservoir.
-------
2
The calculated phosphorus loading of 0.49 g P/m /yr
to Stockton Reservoir is twice the loading proposed by
Vollenweider (1975) for an oligotrophic lake, and less than
Vollenweider's eutrophic loading figure. However, spring
chlorophyll a^ values in the lake (9.7 - 29.2 yg/1) as well as
excessively high spring algal counts indicate a much higher
biological response to existing nutrient levels than would
typically be expected. In light of this demonstrated increase
in spring Take productivity it would be desirable to substan-
tially reduce phosphorus contributions from known point sources
in order to improve lake water quality and decrease the like-
lihood of problem algal blooms or macrophyte growths in the
reservoir.
2. Nonpoint sources -
The total phosphorus load from nonpoint sources accounted
for 58.0% of the total load reaching Stockton Reservoir.
Measured tributaries contributed 23.2%, while ungaged drainage
areas were estimated to have contributed 31.2%.
The phosphorus export rates of the three gaged tributaries
2
to Stockton Reservoir (range of 2 to 13 kg P/km /yr, mean of
2
7 kg/km /yr) were comparable to the rates of the gaged tribu-
taries surveyed in nearby Pomme de Terre Reservoir* (see Section
IV-D).
*Working Paper No. 548
-------
II. LAKE AND DRAINAGE BASIN CHARACTERISTICS
Lake and drainage basin characteristics are itemized below.
Lake morphometric data were provided by the Missouri Clean Water
Commission. Tributary flow data were provided by the Missouri
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 the
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: 100.77
2. Mean depth: 7.3 meters.
3. Maximum depth: >30.5 meters.
4. Volume: 735.621 x 106 m3.
5. Mean hydraulic retention time: 386 days (1.06 yrs).
-------
B. Tributary and Outlet:
(See Appendix B for flow data)
1. Tributaries -
Drainage Mean flow
Name area(km2) (m3/sec)
A-2 Sac River 587.9 4.39
C-l Little Sac River 606.1 4.64
E-l Turnback Creek 525.8 3.88
Minor tributaries and
immediate drainage - 1,183.8 9.74
Totals 2,903.6 22.65
2. Outlet - A-l Sac River 3,004.4 21.97
C. Precipitation:
1. Year of sampling: 110.8 cm.
2. Mean annual: 99.8 cm.
-------
III. LAKE WATER QUALITY SUMMARY
Stockton Reservoir was sampled three times during the open-
water season of 1974 by means of a pontoon-equipped Huey heli-
copter. Each time, samples for physical and chemical parameters
were collected from five stations on the lake and from a number
of depths at each station (see map, page y)- During each visit,
depth-integrated samples were collected from each station for
chlorophyll a^ analysis and phytoplankton identification and enu-
meration. During the first and last visits, 18.9-liter depth-
integrated samples were composited for algal assays. Maximum depths
sampled were 30.5 meters at Station 01, 24.4 meters at Station 02,
20.7 meters at Station 03, 22.9 meters at Station 04, and 16.8
meters at Station 05. 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 a_ determinations are included in III-B. Results of
the limiting nutrient study are presented in III-C.
-------
ST'KKTON
At*0 CrtEMJCAl
F A u? t '• <-. r £ -J
( */ 0/7* )
•1AX
QbPT"
(METEnS)
MAX
S»«* = 3
i£ MEDIAN ("ETEWSI N»
( 10/ 8/7* )
MAX
$»»« = 5 OEPTh
RANGE
*ANGE MEDIAN
O.-l .3 M DEPT-i
MA X
1(1
b
".7- 10. S
y.ft- 10.3
1.0- l.a
16. fl- 30. b
10 ?2.2- 24. b 22.6 0.0- l.b
5 13.4- 21.3 1 7 . Q 1ft. 5- 27.4
9 17.h- 18.2 1^.1 0.0- l.b
b 15.0- 1H.1 17.I 13.7- 25.9
DISSOLVED O'YbEN C10/D
O.-l.b i* r'EPTH S 10.4- 11.2
*« S 10.6- 10.8
CONDUCTIVITY' (IJMHOS)
O.-l.^ ••' OEPTH 10 20S.-
10.tt 1.b- 1 .5
1 0.>5 1ft. e- 30.b
209. 0.0- l.b
209. 16.P- JO.b
10
b
/ . 0 - M . o
0.2- 4.4
7.4 0.0- l.b
0.6 1ft.5- 27.4
10 28H.- 2^4. 290. 0.0- 1.5
S 262.- 304. 2flfl. 16.5- 27.»
b.fl- 7.b
0.0- 7.0
6.4 0.0- l.b
5.8 13.7- 25.si
4 222.- 307. 227. 0.0- 1.5
b 22*.- 279. 229. 13.7- 25.9
Ph (
O.-l ,-j M f/bPTH
MAX Ot'PTH«*
10
5
a. 3- 8.4
8.3- 8.3
TOTAL ALiv4LINITY (M^/L)
O.-l.6-. M DEPTH 10 130.- 134,
MAX DEPTH** b 130.- 135.
-l.J 0.0- 1.5
H.3 16.H- 30.5
13?. 0.0- l.b
134. 16.6- 30.b
10 8.2- 8.6
5 7.5- 8.0
in 129.- 13b.
b 131.- 160.
6.3 0.0- l.S
7.9 16.5- 27.*
132. 0.0- l.b
150. 16.5- 27.4
7.9- (j.l
7.5- 8.0
7.* 0.0- 1.5
7.9 13.7- 25.9
9 122.- 131. 130. 0.0- 1.5
b 121.- 174. 129. 13.7- 25.9
TOTAL P
O.-l.S M DEPTH
MAX
10 0.018-0.036
b 0.020-0.047
DISSOLVED OKTHO P (MG/LI
.O.-l.S M DEPTH 10 0.004-0.006
MAX OtPTH«» S 0.004-0.011
0.02/ 0.0- l.S
0.02V 1ft.8- 30.b
O.Onb 0.0- 1.5
0.006 16.8- 30.5
10 0.014-0.024 0.020 0.0- 1.5
b 0.019-0.06B 0.0*3 16.5- 27.4
7 0.006-0.017 0.01U 0.0- l.S
5 0.012-0.042 0.023 16.5- 27.4
V O.U 14-0.034 0.01* 0.0- l.b
b 0.014-0.20ft 0.03« 13.7- 25.v
9 0.003-0.007 0.004 0.0- 1.5
5 0.004-0.015 0.006 13.7- 25.9
O.-l.S M OEPTn
MAX
AMMONIA (Mfj/L)
O.-l.'-i M DE^TH
MAX
10 0.620-0.^30 0.7?b 0.0- l.b 10 0.4*0-0.610 0.575 0.0- l.b w 0.210-0.350 0.270 0.0- l.b
b O.f.bO-0.880 0.700 16.8- 30.b 5 0.340-0.970 0.500 16..5- 27.4 S 0.020-0.310 0.270 13.7- ?5.9
10 0.030-0.060 0.040 0.0- l.b 10 0.050-0.100 0.065 0.0- l.b 9 0.060-0.100 0.080 0.0- 1.5
b J.OJO-0.060 0.050 16.8- 30.5 5 0.070-0.680 0.480 16.5- 27.4 b 0.050-1.980 O.OflO 13.7- 25.9
KJbLJAHL N (M()/L>
o.-i.'5 M DEPTH
MAX DEr>TH«»
10 0.300-0.600 0.400 0.0- l.b 10 0.300-0.600 0.400 0.0- 1.5 v 0.200-0.ftOO 0.300 0.0- l.b
5 0.300-0.500 0.400 16.8- 30.5 5 0.300-1.100 0.800 16.5- 27.4 5 0.200-2.900 0.400 13.7- 25.9
SECCHI DISC
1.3
l.a- 2.7
2.7
1.2- 2.n
l.H
N = NO. OK SAMPLES
MAXIMUM utVTH CAMPLED AT EACH siTt
= NO. OK SUPS SAMPLED ON THIS UATt
-------
B. Biological Characteristics:
1. Phytoplankton -
Sampling
Date
04/08/74
06/24/74
10/08/74
Dominant
Genera
1. Melosira
2. Stephanodiscus
3. Chroomonas
4. Ankistrodesmus
5. Cryptomonas
Other genera
Total
1. Fragilaria
2. Melosira
3. Chroomonas
4. Cryptomonas
5. Tetraedron
Other genera
Total
1. Melosira
2. Dactylococcopsis
3. Chroomonas
4. Stephanodiscus
5. Cryptomonas
Other genera
Total
Algal
Units
per ml
16,515
3,398
430
387
258
688
21,676
599
436
381
381
163
328
2,288
879
778
744
271
237
779
3,688
-------
2. Chlorophyll a -
Sampling Station Chlorophyll a_
Date Number (yg/1)
04/08/74 01 9.7
02 25.8
03 29.2
04 13.0
05 21.8
06/24/74 01 2.7
02 1.5
03 1.3
04 1.3
05 3.0
10/08/74 01 4.1
02 4.4
03 6.5
04 3.2
05 7.2
-------
10
C. Limiting Nutrient Study:
1. Autoclaved, filtered, and nutrient spiked
a. 04/08/74 - Stations 01-03
Ortho P Inorganic N
Spike(mg/l) Conc.(mg/l) Conc.(mg/l)
Control
0.05 P
0.05 P + 1.0 N
1.00 N
b. 04/08/74 -
Control
0.05 P
0.05 P + 1.0 N
1.00 N
c. 10/08/74 -
Control
0.05 P
0.05 P + 1.0 N
1.00 N
d. 10/08/74 -
Control
0.05 P
0.05 P + 1.0 N
1.00 N
0.005
0.055
0.055
0.005
Stations 04-05
0.005
0.055
0.055
0.005
Stations 01-03
0.005
0.055
0.055
0.005
Stations 04-05
0.005
0.055
0.055
0.005
0.663
0.663
1.663
1.663
0.606
0.606
1.606
1.606
0.290
0.290
1.290
1.290
0.395 .
0.395
1.395
1.395
Maximum Yield
(mg/1-dry wt.)
0.1
1.6
2.3
0.1
1.2
15.4
27.6
1.8
0.3
1.8
10.8
0.1
0.3
6.7
5.2
0.3
-------
11
2. Discussion -
The control yields of the assay alga, Selenastrum capri-
cornutum, indicate that the potential for primary production
in Stockton Reservoir was low at the times of sampling ex-
cept at Stations 04 and 05 during the spring, when it was
high. Increased growth of the test alga in response to an
addition of orthophosphorus indicates that the lake was lim-
ited by phosphorus during both the spring and fall. Spikes
with nitrogen and orthophosphorus simultaneously generally
resulted in maximum yield. Additions of nitrogen alone did
not stimulate growth significantly beyond the control yields.
The N/P ratios in the lake samples were 157/1 in the
spring, 54/1 in the summer, and 75/1 in the fall, further in-
dicating phosphorus limitation.
-------
12
IV. NUTRIENT LOADINGS
(See Appendix D for data)
For the determination of nutrient loadings, the Missouri
National Guard collected monthly near-surface grab samples from
each of the tributary sites indicated on the map (page v), ex-
cept for the high runoff months of May and June when two samples
were collected. Sampling was begun in September 1974, and was
completed in August 1975.
Through an interagency agreement, stream flow estimates for
the year of sampling and a "normalized" or average year were pro-
vided by the Missouri 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" ("ZZ" of USGS) were estimated by using the mean
o
annual nutrient loads, in kg/km /yr, in Turnback Creek, at Station
E-l, and multiplying the means by the ZZ area in km2.
The operators of the Ash Grove, Springfield Northwest, and
Greenfield (three plants) wastewater treatment plants provided
monthly effluent samples and corresponding flow data. Nutrient
loads for the Ash Grove and Willard High Schools were estimated
-------
13
at 0.567 kg P and 1.701 kg N/Capita/yr (180 days). Nutrient
loads for the Republic, Billings, and the remaining small pri-
vate wastewater treatment plants were estimated at 1.134 kg P
and 3.401 kg N/Capita/yr.
-------
14
A. Waste Sources:
1. Known municipal
Name
Ash Grove
Springfield
Northwest
Greenfield
Southwest
Greenfield
Northwest
Greenfield
Southeast
Republic
Lagoon B***
Springfield
Municipal Airportt
Billingst
Lakewood Mobile
Home Parkt
Springfield "44"
Auto Truck Stop
Inc.
Nil lard R-2
High School
Chalet City
Sunshine Acres
Nursing Home
Ash Grove R-4 School
2. Known industrial - See discussion, page 2.
Population
Served*
1,100
20,000
50
150
850
1,000
300
760
245
294
141
450
240
103
Mean Flow
Treatment* (m3/d x 103)
Trickling
f i 1 ter
Activated
sludge
Stabilization
pond
Stabilization
pond
Stabilization
pond
Stabilization
pond
Sand filter
Stabilization
pond
Extended
aeration
Extended
aeration
Stabilization
pond
Extended
aeration
Stabilization
pond
Stabilization
pond
0.725
8.732
0.116
0.107
0.071
0.378**
0.114**
0.288**
0.093**
0.111**
0.053**
0.170**
0.091**
0.039**
Receiving
Water
Sac River
Little Sac
River
Whetzel Branch/
Sons Creek
Whetzel Branch/
Sons Creek
Wilson Branch/
Turnback Creek
Branch of
Pickerel Creek/
Sac River
Clear Creek
Pickerel Creek/
Sac River
Little Sac River
North Dry Sac
River
Losing Stream/
Clear Creek
Branch of Pond
Creek/Sac River
Clear Creek
Sac River
treatment plant questionnaires.
**Estimated at 0.3785 m3/capita/day.
***U.S.EPA, 1971.
tMissouri Department of Natural Resources (manuscript).
-------
15
B. Annual Total Phosphorus Loading - Average Year:
1. Inputs -
% of
Source kg P/yr total
a. Tributaries (nonpoint load) -
A-2 Sac River 930 1.9
C-l Little Sac River 3,810 7.7
E-l Turnback Creek 6,695 13.6
b. Minor tributaries and immediate
drainage (nonpoint load) - 15,390 31.2
c. Known municipal STP's -
Ash Grove 3,815 7.7
Springfield Northwest 12,630 25.6
Greenfield Southwest 280 0.6
Greenfield Northwest 30 0.1
Greenfield Southeast 75 0.1
Republic Lagoon B 1,135 2.3
Springfield Municipal 340 0.7
Airport
Billings 860 1.7
Lakewood Mobile Home 280 0.6
Park
Springfield "44" Auto 335 0.7
Truck Stop Inc.
Willard R-2 High School 80 0.2
Chalet City 510 1.0
Sunshine Acres Nursing 270 0.6
Home
Ash Grove R-4 School 60 0.1
d. Septic tanks* - 5 <0.1
e. Known industrial - See discussion,
page 2.
f. Direct precipitation** - 1,765 3.6
Totals 49,295 100.0
2. Output - A-l Sac River
3. Net annual P accumulation -
*Estimate based on 20 lakeside residences.
"Estimated (see NES Working Paper No. 175).
-------
16
C. Annual Total Nitrogen Loading - Average Year:
1. Inputs -
% of
Source kg N/yr total
a. Tributaries (nonpoint load) -
A-2 Sac River 363,860 20.3
C-l Little Sac River 343,730 . 19.2
E-l Turnback Creek 282,340 15.8
b. Minor tributaries and immediate
drainage (nonpoint load) - 635,700 35.5
c. Known municipal STP's -
Ash Grove 5,710 0.3
Springfield Northwest 38,295 2.1
Greenfield Southwest 615 <0.1
Greenfield Northwest 130 <0.1
Greenfield Southeast 225 <0.1
Republic Lagoon B 3,400 0.2
Springfield Municipal 1,020 0.1
Airport
Billings 2,585 0.1
Lakewood Mobile Home 835 <0.1
Park
Springfield "44" Auto 1,000 0.1
Truck Stop Inc.
Willard R-2 High School 240 <0.1
Chalet City 1,530 0.1
Sunshine Acres Nursing 815 0.1
Home
Ash Grove R-4 School 175 <0.1
d. Septic tanks* - 215 <0.1
e. Known industrial - See discussion,
page 2.
•f. Direct precipitation** - 108,790 6.1
Totals 1,791,210 100.0
2. Output - A-l Sac River 1,106,085
3. Net annual N accumulation - 685,125
*Estimate based on 20 lakeside residences.
**Estimated (see NES Working Paper No. 175).
-------
17
Mean Annual Nonpoint Nutrient Export by Subdrainage Area:
Tributary kg P/knr/yr kg N/km^/yr
Sac River 2 619
Little Sac River 6 567
Turnback Creek 13 537
Mean Nutrient Concentrations in Ungaged Streams:
Mean Total P Mean Total N
Tributary (mg/1) (mg/1)
B-l Slagle Creek 0.027 1.090
D-l Turkey Creek 0.019 0.826
F-l Limestone Creek 0.034 0.945
G-l Sons Creek 0.054 1.005
H-l Walnut Creek 0.026 0.984
Mean phosphorus values in tributary G-l, Sons Creek, are
higher than those found in ungaged tributaries to Stockton
Reservoir. The reason for this phosphorus inflation is not
known.
-------
18
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 Stockton Reservoir 0.49
Vollenweider's eutrophic loading 0.52
Vollenweider's oligotrophic loading 0.26
-------
19
V. LITERATURE REVIEWED
Missouri Department of Natural Resources, manuscript. Water
Quality Management Basin Plan for Osage - Gasconade River
Basin. Water Quality Program, Division of Environmental
Quality, Jefferson City, Missouri.
U.S. Environmental Protection Agency. 1971. Inventory of
Municipal Waste Facilities. EPA Publication #OWP-1, Vol. 7
Office of Media Programs, Office of Water Programs, U.S.
Gov't. Printing Office, 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 Special
Reference to the Phosphorus Loading Concept in Limnology.
Schweiz. Z. Hydrol. 37:53-84.
-------
20
VI. APPENDICES
APPENDIX A
CONVERSION FACTORS
-------
CONVERSION FACTORS
Hectares x 2.471 = acres
Kilometers x 0.6214 = miles
Meters x 3.281 = feet
Cubic meters x 8.107 x 10" = acre/feet
Square kilometers x 0.3861 = square miles
Cubic metors/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
-------
INF..-"'•>&i'
LAKE CODE 29"3 STOCKTON
TOTAL DRAINAGE
SUB-DRAINAGE
TRIBUTARY ARC A (SO KM)
OF LAKK'SQ KM) 3004.;
JAN
PER
APR
MAY
NORMALIZED FLOwS(CMS)
JU'N JUL AuG
00 T
NO i/
DEC
'MEAN
2903A1
2903A2
2903C1
2903E1
2903ZZ
3004.4
587.9
606.1
5?5.fi
1284.6
16.7^
3.48
3.68
3.06
7.70
28. H8
5.10
5.49
4.59
11. 44
12.57
7.31
7.76
6.^8
16.25
28.15
8.10
3.41
7.19
17.67
46.70
8.86
9.43
7.90
19.77
33.13
5.52
5.80
4.93
12.26
32.56
3.65
4.02
3.4b
6.55
1 1.8<+
1.56
1.67
1.39
3.^8
15.72
2.21
2.35
1.59
4.64
10.96
2.46
2.58
2.21
. 5.47
19.62
2.27
2.38
1.98
S.ul
5.64
2. 10
2.24
1.87
4.67
21.97
4.39
4.64
3.88
9.74
SUMMARY
TOTAL DRAINAGE AREA OF LAKE = 3004.4
SUM OF SUB-DRAINAGE AREAS = 3004.^
TOTAL FLOW IN
TOTAL FLOW OUT
MEAN MONTHLY FLOwS AND DAILY FLOWS(CMS)
TRIBUTARY MONTH YEAR MEAN FLOW DAY
290JA1
FLOW DAY
FLOW DAY
FLOW
2903A2
9
10
11
12
1
?
3
4
5
6
7
8
9
•10
11
12
1
2
3
4
5
6
7
8
74
74
74
74
75
75
75
75
75
75
75
75
74
7<»
74
74
75
75
75
75
75
75
75
75
30.582
5.918
19.171
39.077
59.465
68.527
117.232
107.604
43.891
21.011
12.318
8.042
4.814
1.557
3.681
1.841
4.955
16.424
23.22C
7.929
16.565
5.012
1.926
C.878
14
19
2
14
11
1
1
20
4
8
13
3
14
19
2
14
11
1
1
20
4
8
13
3
2.662
0.878
1.303
1.416
7.447
1.416
93.446
- 1.274
5.635
1.133
1.218
1.926
2.124
2.832
3.398
7.9?9
9.911
45.307
28.317
5.522
5.663
2.265
1.274
0.708
18
22
18
22
3.710
1.048
3.115
3.540
272.38
264.56
-------
7. 8'jT Af-'r KLUW !NFiji
-------
APPENDIX C
PHYSICAL AND CHEMICAL DATA
-------
/TY?A/AMdNT/LA«E
DATE
FROM
TO
7<*/04/oa
74/U6/24
74/10/08
TIME DEPTH
OK
DAY
09
09
09
09
09
10
10
1C
10
10
10
10
10
10
10
10
10
10
10
F
iO
40
40
40
40
45
45
45
45
45
45
45
45
45
45
45
45
45
45
EET
0000
0005
0015
0050
0100
0000
0005
0028
0045
0055
0090
0000
0005
0015
0030
0045
0060
0075
ooes
00010
WATER
TEMP
CENT
9.9
9.9
9.9
10.0
9.9
22.3
22.2
22.0
21.8
21.8
21.3
18.2
18.2
18.2
18.2
18.2
18.1
18.1
18.1
290301
37 41 23.0 U93 45 54.0
STOCKTON "•ESE^VOI*
29V39 MISSOURI
091491
llEPALcS 04001002
OlOb FEET OfPTn CLASS
00300
DO
MG/L
10.6
10.8
10.6
10.6
7.0
7.0
6.8
4.8
5.6
4.4
6.8
7.6
7.0
6.8
7.2
7.0
7.0
7.0
00077 00094
fKANSP CNOUCTVY
SECChI FIELD
INCHES MICWOMHO
65 210
210
210
210
210
106 290
288
289
288
290
288
78 222
231
228
230
230
230
230
229
00400
PH
SU
8.30
8.3C
8.30
8.30
8.30
8.40
8.30
8.30
8.2C
8.10
8.00
8. 1C
8.05
8.05
8.05
8.05
8.00
8.00
8.00
00410
T ALK
CAC03
MG/L
132
132
131
135
134
134
135
137
137
138
131
131
130
129
129
128
129
128
128
00610
NH3-N
TOTAL
MG/L
0.030
0.040
0.030
0.060
0.040
0.080
0.080
0.070
0.060
0.070
0.070
0.080
0.060
0.050
0.060
0.050
0.060
0.050
0.050
00
00625
TOT KJEL
N
MG/L
0.500
0.300
0.300
0.300
0.300
0.500
0.300
0.300
0.300
0.300
0.400
0.600
0.300
0.300
0.300
0.400
0.300
0.300
0.400
00630
N02&N03
N-TuTAL
MG/L
0.730
0.720
0.700
0.710
0.700
0.560
0.590
0.590
0.620
0.630
0.580
0.210
0.220
0.220
0.220
0.220
0.230
0.220
0.220
00671
PhOS-UIS
OhiTrtO
MG/L P
0.005
0.005
0.005
0.005
0.006
0.008
0.008
0.007
0.012
0.007
0.005
0.004
0.004
0.004
0.004
0.004
0.004
-------
RETRIED;. OATc
290J01
37 41 23.C 093 45 54.0 3
STOCK.TON RESEWVOlK
29039 MISSOURI
11EPALES
0105 FEET
04001002
CLASS 00
DATE
FROM
TO
74/04/OB
74/06/24
74/10/08
OJ665 32217 00031
TIME DEPTH PhOS-TOT CHLRPHYL INCDT LT
OF A PENNING
OAY FEET MG/L P
09
09
09
09
09
10
10
10
10
10
10
10
10
10
10
10
10
10
10
10
10
40
40
40
40
40
45
45
45
45
45
45
45
45
45
45
45
45
45
45
45
45
0000
0005
0015
0050
0100
0000
OOOb
0028
0045
0055
0090
OO'JO
OOJ3
0005
0011
0015
0030
0045
0060
0075
0085
0
0
0
0
0
I)
0
0
0
0
0
'J
0
0
0
0
0
0
0
.021
.023
.022
.022
.022
.0 1<«
.016
.016
.018
.015
.019
.016
.014
.013
.013
.013
.013
.013
.014
UG/L PERCENT
9.7
2.7
4.1
50.0
5.0
1.0
-------
n'tlTRitV-V.. OAli
/TYPA/AM8NT/LA«r
DATE
FROM
TO
74/04/08
74/06/24
74/10/08
TIMF
OF
DAY
10
10
10
10
10
12
12
12
12
12
12
12
11
11
11
11
11
11
IS
15
15
15
15
40
40
40
40
40
40
40
30
10
30
30
TO
30
DEPTH
FEET
0000
0005
0015
0040
0065
0000
0005
0025
0035
0047
0065
ooao
0000
0005
0015
0030
0045
0052
00010
WATER
TEMP
CENT
9.7
9.7
9.7
9.7
9.8
22.6
22.6
21. a
20.6
1B.1
14.6
13.6
18.1
17.9
17.8
17. fl
17.8
17.7
37 36 36.0 093 45 52.0 3
STOCKTON
091491
HE-ALcS
G400
0070 FEET OEPTn CLASS
00300
DO
MG/L
10.8
10.8
10.8
10.8
7.2
7.0
5.4
3.4
0.6
0.2
0.2
6.0
6.6
5.8
5.8
5.8
5.8
00077 00094
TRANSP CMOUCTVY
SECCHI FIELD
INCHES MICROMHO
50 208
209
209
209
209
108 290
290
287
283
275
263
262
72 o 225
225
224
224
225
224
00400
PH
su
8.30
8.30
8.30
8.30
•8.3C
8.20
8.30
8.10
8.00
7. 80
7.83
7.60
8.00
7.9C
7.90
7.90
7.90
7.90
00410
T ALK
CAC03
MG/L
" 134
134
133
133
131
132
131
130
132
138
143
150
131
130
128
129
128
129
00610
NH3-N
TOTAL
MG/L
0.050
0.060
0.050
0.050
0.050
0.080
0.070
0.080
0.080
0.100
0.230
0.480
0.080
0.060
0.060
0.060
O.ObO
0.060
1002
00
00625
TOT KJEL
N
MG/L
0.500
0.400
0.400
0.400
0.400
0.500
0.400
0.300
0.400
0.400
0.500
0.800
0.400
0.200
0.200
0.200
0.300
0.200
00630
N02&N03
M-TOTAL
MG/L
0.800
0.800
0.780
0.800
0.790
0.600
0.610
0.660
0.730
0.830
0.690
0.500
0.300
0.300
0.310
0.310
0.310
0.310
00671
PHOS-OIS
ORTHO
MG/L r>
0.006
0.005
0.005
0.006
0.006
0.011
0.011
0.009
0.014
0.013
0.017
0.003
0.003
0.003
0.004
0.004
0.004
-------
37 36 36.0 093 45 52.0 3
STOCKTON StSE«VOI»
29039 MISSOURI
XTVPA/AM8NT/L4KF.
DATE
FROM
TO
74/04/03
74/06/24
74/10/08
00665 32217 00031
TIME DEPTH PhOS-TOT CHLRPnyL INCOT LT
OF ' A HEMNING
DAY FEET
10
10
10
10
10
12
12
12
12
12
12
12
11
11
1
1
1
1
1
1
1
15
15
15
15
15
40
40
40
40
40
4!5
40
30
30
30
30
30
30
30
30
30
0000
0005
C015
0040
0065
0000
0005
0025
0035
0047
0065
ooao
0000
0002
0005
0006
0010
OOlb
0030
0045
0052
MG/L P UG/L PERCENT
0
0
0
0
G
0
0
0
0
0
0
0
0
0
0
0
0
0
.032 25.8
.02H
.026
.026
.029
.016 1.5
.021
.022
.025
.031
.026
.052
.015 4.4
.014
.01<4
.015
.016
.019
50.0
5.0
1.0
11CPALES
0070 FEET
C4C01002
CLASS 00
-------
W ;<-;vAI. I'
DATE
FROM
TO
74/04/08
74/t)6/,?4
74/10/08
TIME
OF
DAY
12
12
12
12
12
13
13
13
13
13
13
12
12
12
12
12
12
05
05
05
05
0^
05
05
05
05
05
05
10
10
1C
10
10
10
OEPT-i
FEET
0000
0005
0015
0040
0065
0000
OOOS
0015
0035
0050
0068
0000
0005
0015
0035
0050
0062
00010
WATER
TEMP
CENT
10.4
10.4
10.4
10.3
10.3
22.5
22.5
22.4
21.3
18. a
18.2
18.0
17.8
17.7
17.7
17.5
17.5
^90303
37 32 08.0 093 47 3b.O 3
STOCKTON RESERVOIR
?9^S7 -iSSOUPI
091491
00300
DO
MG/L
1C. 8
10.8
10.8
10.8
7.4
7.4
6.8
4.6
1.8
1.4
6.4
6.2
6.4
5.8
5.6
4.0
00077 00094
TRANSP CNOUCTVY
SECCHI FIELD
INCHES MICROMHO
35 210
210
210
210
210
72 290
289
. 289
284
286
293
48 227
225
224
224
223
229
1 lE?i
007
00400
Prl
SU
8.30
8.30
8.30
8.30
8.30
8.20
8.4Tri CLASS
00410
T ALK
CAC03
MG/L
132
132
131
132
134
133
132
130
134
144
146
130
131
131
130
131
134
00610
NH3-N
TOTAL
MG/L
0.050
0.040
0.060
0.040
0.030
0.060
0.050
0.060
0.080
0.100
0.130
0.060
0.060
0.110
0.060
0.090
U.200
1002
00
00625
TOT KJEL
N
MG/L
0.600
0.400
0.500
0.500
0.400
0.500
0.400
0.500
0.400
0.300
0.300
0.300
0.200
0.200K
0.300
0.300
O.tOO
00630
N02MM03
N- TOTAL
MG/L
0.930
0.930
0.920
0.900
0.880
0.590
0.590
0.610
0.810
0.930
0.970
0.340
0.350
0.380
0.330
0.340
0.290
00671
PnOS-DIS
ORTrlO
MG/L P
0.005
0.006
0.007
0.006
0.011
O.OOb
0.006
0.00 7
0.010
0.051
0.042
0.004
0.004
0.004
0.006
0.005
0.006
K VALUE KNOrfN TO Bt
LESS THAN INDICATED
-------
77/!i.V2»
DATE
FROM
TO
74/C6/24
74/io/oa
290303
37 32 08.0 093 47 36.0 3
STOCKTON «tSFKVOI«
?40S7 MISSOURI
091491
lltr'iLtS
0071 FEET
C40010C2
CLASS 00
C0665 32217 00031
TIME DEPTH PHOS-TOT CHLRPHYL INCOT LT
OF a REINING
DAY FEET
12
1?
12
12
12
13
13
13
13
13
13
1?
12
12
12
12
12
05
05
05
05
05
05
05
05
05
05
05
10
10
10
10
10
10
0000
0005
0015
0040
0065
0000
0005
0015
0035
0050
0068
0000
0005
0015
0035
0050
0062
MG/L
0
0
0
0
0
c
c
0
0
0
0
0
0
0
0
0
0
•
*
•
•
•
*
•
•
„
*
•
*
•
•
•
•
•
P
033
036
036
044
047
021
022
021
027
050
043
023
023
020
027
030
049
UG/L PERCENT
29.2
1.3
6.5
-------
s-.r.3FT «
AT? 77,' ;•
00010
DATE TIMF DEPTH *ATER
FROM OF TEMP
TO DAY FEET
74/04/08 12
12
12
12
12
74/0^/?«< 10
10
1C
10
10
10
74/10/08 09
09
09
09
09
09
09
5C
50
50
5C
50
05
05
05
05
05
05
55
55
55
55
55
55
55
0000
0005
0015
0040
0075
0000
0005
0023
0040
0055
0071
0000
0005
0015
0035
0050
0060
0067
CENT
9.9
9.9
9.9
9.9
9.6
23.7
23.7
23.1
19.4
14.4
13.4
18.1
18.1
18.1
18.1
18.0
15.6
15.0
2=0304
37 36 15.0 093 42 58.0 3
STOCKTON rVE
091491
1 IL'^I
^L£ s
0400
0030 FErlT DEPTH CLASS
00300
00
MG/L
10.4
10.8
10.4
i ;•/ . 6
8.4
8.4
7.6
1.0
C.2
0.4
5.8
6.0
6.0
5.8
5.6
0.1
0.0
OOC77 00094
TRANSP CfMOMCTVY
SECCHI FIELD
INCHES MlCPOMHO
60 206
206
207
208
208
106 293
294
293
283
262
266
72 233
307
236
236
232
276
279
00400
HH
SU
8.30
8.30
8.30
8.30
8.30
8.4.1
8.40
8.40
7.90
7.90
7.90
7.90
7.90
7.90
7.20
7.90
7.60
7.55
00410
T ALK
CAC03
MG/L
132
132
134
134
135
131
134
134
139
147
154
123
124
125
128
127
159
174
00610
NH3-N
TOTAL
MG/L
0.040
0.030
0.040
0.060
0.060
0.100
0.050
0.030
0.080
0.230
0.590
0.090
0.100
0.090
0.060
0.080
1.660
1.980
1002
00
00625
TOT KJEL
N
MG/L
0.400
0.400
0.300
0.300
0.300
0.400
0.300
0.400
0.300
0.400
0.900
0.400
0.300
0.300
0.300
0.500
1.800
2.900
00630
N02&N03
N-TOTAL
MG/L
0.640
0.620
0.630
0.650
0.650
0.520
0.520
O.b40
0.750
0.740
0.340
0.250
0.250
0.240
0.250
0.240
0.030
0.020K
00b71
PnOS-OIS
ORTHO
MG/L P
0.004
0.004
0.004
0.004
0.004
0.012
0.008
0.010
0.010
0.032
0.004
0.004
0.006
0.007
0.009
0.010
0.015
K VALUE K-JOWN TO BE
LESS in'A.N INDICATED
-------
DATE
FROM
TO
74/04/08
74/06/24
74/10/08
OC665 32217 00031
TIME DEPTH PHOS-TGT CHLRPHYL INCOT LT
OF A RtHNING
DAY FEET
12
12
12
12
12
10
10
10
10
10
10
09
09
09
09
09
09
09
SO
50
50
50
SO
OS
05
05
05
05
05
55
55
55
55
55
55
55
0000
0005
0015
0040
0075
0000
0005
0023
0040
0055
0071
0000
0005
0015
0035
0050
0060
0067
MG/L M UG/L PERCENT
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
.018 13.0
.020
.021
.022
.020
.019 1.3
.015
.016 l.u
.019
.016
.042
.020 3.2
.019
.02-4
.023
.027
.117
.206
290304
37 36 15.0 093 42 58.0 3
STOCKTON RESERVOIR
29039
091491
11EPALES
FEET
QE°TH
040C1002
CLASS 00
-------
TO P. El SL'TPiEVAL OATF ??./ut/2-t
290305
37 34 08.0 C93 39 22.0 3
STOCKTON RESE
29,157 MISSOURI
C914V1
/TYPA/AMBNT/LAK"
11EPALES 04001002
0060 FEET DEPTH CLASS 00
DATE
FROM
TO
74/04/08
74/06/24
74/10/08
DATE
FROM
TO
74/04/08
74/06/24
74/10/oa
TIME DEpTH
OF
DAY FEET
13 25 0000
13 25 0005
13 25 0015
13 25 0030
13 25 0055
09 30 0000
09 30 0005
09 30 0010
09 30 0035
09 30 0054
09 15 0000
09 15 0015
09 15 0030
09 15 0045
TIME DEPTH
OF
DAY FEET
13 25 0000
13 25 0005
13 25 0015
13 25 0030
13 25 0055
09 30 0000
09 30 0005
09 30 0010
09 30 0035
09 30 0054
09 15 0000
09 15 0015
09 15 0030
09 15 0045
00010
WATER
TEMP
CENT
10.5
10.5
10.5
10.4
10.3
2*. 5
24.4
24.0
20.7
17.9
18.0
1H.O
18.0
18.0
00665
PHOS-TOT
MG/L P
0.026
0.032
0.032
0.029
0.031
0.024
0.021
0.017
0.027
0.06H
0.034
0.030
0.030
0.038
00300
00
MG/L
11.
10.
10.
10.
8.
8.
3.
0.
0.
6.
6.
6.
6.
32217
00077
TRANSP
SECCHI
INCHES
50
2
8
8
8
6 96
6
6
8
6
6 48
2
6
4
00031
00094
CNOUCTVY
FIELD
MICROMHO
205
205
205
205
20fa
294
294
296
300
304
233
231
232
233
00400
PH
SU
8.4C
8.40
8.30
8.30
8.30
8.60
8.30
8.30
7.6P
7.50
'7.95
7.95
8.00
7.90
00410
T ALK
CAC03
MG/L
131
130
130
129
130
129
129
133
144
160
122
122
124
121
00610
NH3-N
TOTAL
MG/L
0.040
0.040
0.060
0.050
0.060
0.060
0.050
0.080
0.180
0.680
0.080
0.080
0.120
0.080
00625 00t>30
TOT KJEL N02t^03
N N-TOTAL
MG/L
0.600
0.400
0.400
0.500
0.500
0.600
0.300
0.300
0.400
1.100
0.300
0.200K
0.300
0.400
MG/L
0.690
0.700
0.720
0.700
0.700
0.480
0.480
0.540
0.680
0.390
0.270
0.280
0.280
0.270
00671
PHOS-DIS
ORTHO
MG/L P
0.004
0.004
0.005
0.004
0.006
0.017
0.010
0.011
0.014
0.023
0.006
0.006
0.007
0.007
CHLRPHYL INCDT LT
A
UG/L
21.
3.
7.
REMNING
PERCENT
fi
0
1.0
2
•
K VALUE K'JOW.-J 70 B-L
!_E5S THAN
-------
APPENDIX D
TRIBUTARY AND WASTEWATER
TREATMENT PLANT DATA
-------
S70RET r<
/TYPA/AXBNT/ST»EAM
2vo3Ai
37 42 03.0 093 45 20.0 4
SAC RIVER
29 7.5 STOCKTON
0/STGCK.TON RESERVOIR 091491
MO H*Y 32 tfRDG 2 MI E OF STOCKTON
IIE^ALES 04001004
0000 FEET DEPTH CLASS 00
DATE TIME DEPTH N026.N03
FROM OF ,
TO DAY FEET
74/C9/14
74/10/19
74/11/02
74/12/14
75/Ol/U
75/02/01
75/03/01
75/04/20
75/05/04
75/05/18
75/06/08
75/06/22
75/07/13
75/08/03
15
14
13
1?
10
11
11
13
14
12
11
10
12
10
30
30
45
20
30
00
so
45
45
15
50
10
30
00
0630
'6.N03
OTAL
IG/L
0.056
0.272
0.304
0.400
0.368
0.352
0.432
0.035
0.735
0.670
0.575
0.530
0.440
0.960
00625
TOT KJEL
N
MG/L
0.300
0.900
0.600
1.100
1.600
1.400
1.650
0.150
1.680
0.350
0.650
0.350
0.550
0.900
00610
NH3-N
TOTAL
MG/L
. 0.072
0.030
0.050
0.015
0.136
C.032
0.032
0.010
0.025
0.025
0.030
O.C10
0.030
0.040
00671
PHOS-DIS
OP.THO
MG/L P
0.005K
0.010
0.015
0.005K
0.005K
(1.016
0.008K
0.005K
0.005
0.005K
0.005K
O.OOSK
0.010
00665
PHOS-TOT
MG/.L r>
0.020
0.015
0.020
0.020
0.010*
0.040
0.020
0.010K
0.020
0.010K
0.020
0.010
0.010
0.090
K VALUE KiNlOWN TO tit
LESS THAN INDICATED
-------
290 JA2
37 23 52.0 093 38 00.0 4
?9 7.S DAUEvlLLE
T/STOCKTON RESERVOIR 091491
SEC *D BH')G AT COMET
11EPALES C40C100H
000!) FEET DEPTH CLASS 00
DATE TIME DEPTH N02S.N03
FROM OF
TO DAY FEET
74/09/14
74/10/19
74/11/02
74/12/14
75/C1/11
75/02/01
75/03/01
75/04/20
75/05/04
75/05/18
75/06/08
75/06/22
75/07/13
75/08/03
12 ?5
11 10
08 45
14 20
13 ?S
09 40
14 25
10 40
16 08
13 45
14 35
09 00
11 00
09 45
0630
S.N03
OTAL
G/L
1.700
1.600
1.400
1.920
1.8RO
.780
.950
.720
.800
.950
2.000
1.800
1.800
1.650
00625
TOT KJEL
N
MG/L
0.700
0.800
0.600
0.600
1.000
1.800
1.400
1.050
0.700
1.150
0.450
1.250
0.550
0.850
00610
NH3-N
TOTAL
MG/L
0.030
C.025
0.050
0.010
0. 136
0.690
0.016
0.155
0.035
0.040
0.035
0.030
0.020
0.030
00671
PriOS-OIS
ORTHO
MG/L P
0.035
0.025
0.040
0.010
0.020
0.032
0.024
0.005K
0.010
0.015
0.040
0.045
0.040
0.055
00665
PHOS-TOT
MG/L P
0.050
0.045
0.040
0.020
0.040
0.100
0.070
0.020
0.020
0.030
0.100
0.100
0.060
0.120
K VALUE f^NOwN TO 8E
LESS THAN INDICATED
-------
'. OA7C 77/0
-------
O.M'f 77/CP/24
/TYPA/AMUNT/STPI
DATE TIME DEPTH
FROM OF
TO DAY FEET
2903C1
37 27 33.0 093 28 10.0 4
LITTLE SAC RIVER
?9 7.D MOKSISvILLE
T/STOCKTCN SESERvOIr^ 100391
SEC *D 9*00 3.a MI Sw OF MORKlSVILLE
11EPALES 04001004
0000 FEET DEPTH CLASS 00
74/09/14
74/10/19
74/11/02
74/12/14
75/01/11
75/02/02
75/03/01
75/04/20
75/05/04
75/05/18
75/06/08
75/06/22
75/07/13
75/08/03
10 20
10 00
09 03
11 00
11 00
08 50
10 30
11 27
10 19
09 30
10 00
08 50
09 45
09 00
0630
OTAL
G/L
1.760
1.320
1.120
1.360
1.180
0.4?5
1.150
1.300
1.500
1.700
1.700
1.800
1.720
1.150
00625
TOT KJEL
N
MG/L
0.600
1.000
1.200
1.200
2.300
3.000
1.200
0.750
0.950
0.550
0.350
0.750
0.500
2.500
00610
NH3-N
TOTAL
MG/L
0.015
0.045
0.055
0.035
f.232
0.120
0.056
0.025
0.085
0.085
0.035
0.015
0.020
0.065
00671
PHOS-DIS
ORTHO
MG/L P
0.140
0.130
0.050
0.063
0.048
0.032
0.040
0.080
0.095
0.170
0.110
0.140
0.135
00665
PHOS-TOT
MG/L P
0.170
0.155
0.160
0.070
0.100
0.050
0.070
0.070
0.090
0.120
0.220
0.160
0.160
0.230
-------
i. OATL:
37 29 40.0 093 34 50. U 4
S9 7.5 WALNUT GROVE
T/STOCKTON RESERVOIR 091491
bEC RD dROG 2.5 MI Nw OF EUUOHA
11EDALES 04001004
0000 FEET OEPTn CLASS 00
DATE TIME DEPTH N02S.N03
FROM OF
TO DAY FEET
74/0^/14
74/10/19
74/11/02
74/12/14
75/0 I/11
75/02/01
75/03/01
75/04/20
75/05/04
75/05/18
75/06/08
75/06/2?
75/07/13
75/08/03
11 35
13 30
14 30
11 35
09 45
10 ?0
10 15
11 50
11 30
10 40
10 40
09 55
09 50
09 00
0630
S.N03
OTAL
IG/L
0.900
0.672
0.432
0.960
0.890
1.140
0.630
0.610
0.530
0.680
0.680
0.750
0.790
0.790
00625
TOT KJEL
N
MG/L
0.100K
0.600
0.300
0.700
1.700
2.100
0.900
1.300
0.700
0.450
0.600
0.450
0.800
0.950
OOfclO
NH3-N
TOTAL
MG/L
C.015
0.030
0.020
0.007
0.224
0.048
0.024
0.040
0.125
0.020
0.025
0.082
0.040
0.025
00671
PhOS-DIS
ORTHO
MG/L P
0.010
0.015
3.015
0.010
0.012
0.024
0.008K
0.010
0.010
0.010
0.010
0.025
0.015
00665
PHOS-TOT
MG/L P
0.015
0.020
0.015
0.010
0.020
0.040
0.030
0.010
0.010
0.010
3.010
0.030
0.015
0.030
K VALUE r\NO««N TO 6£
LESS THAN INDICATED
-------
.VtTRIfVAi. OATI' 77
37 ?3 03.0 093 47 56.0 4
TU^fJdACK CHEEK
?9 7.5 G-VEEr-FlELU
T/srGCK,TO.N HESEHvOIR 091<+91
UNI^PSOVEd *0 AING AT FIOOLEWS
11EPALES 040C1004
0000 PEfT OEPTn CLASS 00
DATE TIME DEPTH NOaNN03
FROM OF
TO DAY FEET
14 on
10 45
09 35
11 45
12 45
10 30
10 55
09 00
13 35
12 45
13 55
13 20
10 20
11 00
74/10/19
74/11/02
74/13/14
75/01/11
75/02/01
75/03/01
75/04/20
75/05/03
75/05/18
75/06/0«
75/06/2?
75/07/13
75/08/03
20630
?NN03
rOTAL
1G/L
1.320
1.240
0.900
1.600
1.260
1.410
1.350
1.350
1.350
1.570
1.400
1.400
1.200
1.150
00625
TOT KJEL
N
MG/L
0.700
0.400
0.500
1.000
2.100
1 .100
1.300
1.900
0.250
1.1 SO
0.450
0.750
0.450
1.400
00610
NH3-N
TOTAL
MG/L
0.035
0.020
0.065
0.015
0.216
0.166
0.256
0.035
0.035
0.050
0.035
0.040
0.015
0.490
00671
PnOS-DIS
ORTHO
MG/L o
0.035
0.015
0.015
0.010
0.012
0.032
0.024
0.005
0.010
0.010
0.040
0.030
C.025
0.025
00665
PHOS-TOT
MG/L P
0.070
0.030
C.040
0.020
0.050
0 . 1 20
0.070
C.030
0.020
0.030
0.090
0.070
0.050
0.080
-------
2503F1
37 23 05.0 093 49 09.0 4
LIMESTONE CREE^
29 7.5 GREENFIELD
T/srOCKTON -yESESVOIK 091491
SEC SD 3KOG 1.4 .MI NE OF S GREENFIELD
11EPALES 04001004
0000 FEET Dc^TH CLASS 00
DATE TIME DEPTH N02(»N03
FROM OF
TO DAI FEET
74/09/ 14
74/10/19
74/11/02
74/12/14
75/01/11
75/02/01
75/03/01
75/04/20
75/05/03
75/05/lti
75/06/08
75/06/22
75/07/13
75/08/03
13 45
10 30
09 30
11 30
12 25
10 15
10 45
09 15
11 45
13 20
13 45
12 40
10 15
10 30
0630
'i,N03
OT4L
IG/L
1.600
1.080
1.330
1.520
1.420
1.630
1.^00
3.010
1.100
1.250
1.300
1.250
0.640
0.840
00625
TOT KJEL
N
MG/L
0.200
O.BOO
0.600
1.100
1.700
1.200
1.100
1.350
0.200
0.350
1.130
0.650
1.300
0.500
00610
NH3-M
TOTAL
MG/L
0.010
0.035
0.020
0.025
0.060
0.352
0.112
0.060
0.025
0.035
0.065
O.C30
0.095
0.145
00671
PHOS-DIS
ORTMO
MG/L P
0.020
0.020
0.020
0.015
0.010
0.024
0.006
0.015
0.012
0.015
0.025
0.030
0.025
0.030
00665
PMOS-TOT
MG/L P
0.035
0.035
0.030
0.020
0.010
0.060
0.040
0.030
0.020
0.030
0.065
0.060
0.030
0.080
-------
xi.TWIEVAL. fiAf't
37 27 19.0 093 53 b6.0 4
bONS OEE-v
T/STGCivTON -^ESE^tfOl-i OSI1492
CO ^0 rid d^OG 4.1 MI NvV OF G^EENFIELU
llr.DiLES G400100<*
0000 FEET OE^T^ CLASS 00
DATE
FROM
TO
74/09/14
74/10/19
74/11/02
74/12/14
75/01/11
75/02/01
75/03/01
75/04/19
75/05/03
75/05/18
75/06/08
75/06/22
75/07/13
00630 00625
TI"E DEPTi NO?J>N03 TOT KJEL
OF N-TOTAu N
L)A>
14
11
10
12
12
11
10
09
10
13
13
11
09
r FEET
40
^5
15
30
00
00
30
45
02
40
?0
on
20
MG/L
:i
0
0
i
ij
!
0
0
0
0
•s
V
C
1)
.440
.490
.576
.160
.842
.150
.720
.390
.410
.315
.170
.450
.015
MG/L
0.
0.
0.
I.
2.
1.
1.
1.
0.
0.
0.
0.
0.
700
flOO
600
300
000
500
400
SCO
050
425
350
850
487
00610 00671 00665
I\H?-N PIOS-OIS PHOS-TOT
TOTAL ORTHO
MG/L
0.
0.
0.
0.
1.
3.
o.
c.
0.
0.
0.
0.
0.
020
C70
040
010
219
176
040
055
030
030
030
350
037
MG/L
0.
0 .
0.
0.
0.
0.
0.
0.
c.
0.
0.
0.
0.
a
015
020
030
015
040
032
024
010
010
010
010
035
010
MG/L P
0.035
O.OHU
0.060
0.030
0.127
O.CdO
0.0 70
0.030
0.020
0.030
0.050
0.080
0.045
-------
-'t.TS iEvAL CATrf
2S03H1
37 32 05.0 093 30 05.0 4
WALNUT CREEK
29 ,'.a ALORICH
T/STUCKTCiM RESERVOIR 091491
SEC RD 8ROG JUST at OF CAMPGROUND CHURCH
11EPALES . 04001004
0000 FEET DEPTr1 CLASS 00
DATE
FROM
TO
74/00/14
74/10/19
74/11/02
74/12/14
75/01/12
75/02/02
75/03/01
75/04/20
75/05/03
75/05/18
75/06/08
75/06/22
75/07/13
75/U8/03
TIME OEPTr
OF
DAY FEET
11
10
10
10
11
00
10
14
13
10
11
09
09
11
05
45
00
00
30
15
00
30
15
00
10
?5
10
00
4)0630 00625
1 N02f>N03 TOT KJEL
N-TOTAL N
MG/L
Q
0
0
0
0
0
1
0
0
0
0
0
0
0
.044
.016
.016
.192
.176
.250
.200
.690
.020
.045
.075
.045
.080
.960
MG/L
0.
1.
0.
0.
3.
1.
1.
0.
0.
0.
0.
0.
1.
1.
600
300
700
550
100
700
050
350
350
250
100
450
000
250
00610 00671 00665
NH3-N PHOS-DIS PnOS-TOT
TOTAL ORTHO
MG/L
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
020
020
025
005
024
040
192
015
015
145
015
130
030
343
MG/L
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
P
005K
005K
005K
005
005K
006
032
005K
005
005K
005K
010
005K
010
MG/L P
0.010
0.005
0.010K
0.010
0.010K
0.010
0.090
0.020
0.010
0.010K
0.020
0.010
0.010K
0.080
* YALUF KNOWN TO BE
LESS THAN INDICATED
-------
bi'OKCT
77/0?/?'*
POOllOO
37 19 00.0 093 3b 15.0 4
ASH GROVE
29 7.5 ASri GKOVE
T/STOCKTO-J --
74/11/07 15 30
74/12/03 11 00
CP-
74/12/03 16 OC
75/01/10 11 00
CP(T)-
75/01/10 16 00
75/02/10 11 00
CP(T)-
75/02/10 16 00
75/03/11 11 00
CP-
75/03/11 15 00
75/04/15 11 00
CP(T>-
75/04/15 16 00
75/05/08 11 00
CP(T)-
75/05/08 16 00
75/06/12 11 00
75/07/10 13 00
CP(T)-
75/07/10 15 00
75/08/07 11 00
CP(T)-
75/08/07 16 00
75/09/12 11 00
CPITl-
75/09/12 15 00
75/10/09 11 00
CP-
75/10/09 16 00
75/11/13 11 00
CP(T)-
75/11/13 16 00
00630
N02NN03
N-TOTAL
MG/L
5.280
2.960
0.960
1.280
0.800
0.750
2.700
4.000
8.800
11.500
1 J.OOO
6.700
10.000
00625
TOT KJF.L
N
MG/L
4.500
27.000
15.000
2.000
20.000
23.000
21.000
10.500
16.800
9.400
14.000
19.000
17.000
00610 00671 00665 50CS1 50053
NH3-N PHOS-OIS PHOS-TOT FLOW CONDUIT
TOTAL ORTHO • RATE FLOW-MOO
MG/L MG/L P MG/L P INST MOD MONTHLY
13.500
4.000
3.840
7.800
5.150
1.900
2.600
7.900 11.000
22.000
0.250
0.110
0.150
Q.700 10.500 0.100 0.150
5.000 6.200 0.150 0.110
4.309 4.800 0.200 0.150
4.500 6.200 0.170 0.150
0.130
3.900 12.000 0.100 0.110
0.220 10.000 13.000 0.100 0.120
1.300 12.300 15.000 0.100 0.110
0.230 14.500 16.500 0.100 0.100
0.660 7.000 d.90U 0.150 0.100
2.300 15.000 15.500 0.100 0.110
1.000 1.000
-------
DATE
/AMdNT/STREAM
00630
DATE TIME DEPTH N02«.N03
FROM OF N-TOTAL
TO DAY FEET MG/L
74/11/30 00 00
CP-
74/11/30 24 00
74/12/31 00 00
CP(T>-
74/12/31 24 00
75/01/30 24 00
CP(T)-
75/01/31 24 00
75/02/27 24 00
CP ( T ) -
75/02/28 24 00
75/03/30 24 00
CPU)-
75/03/31 24 00
75/04/29 24 00
CP(T)-
75/04/30 24 00
75/05/14 24 00
CP(T)-
75/05/15 24 00
75/05/30 24 00
cpm-
75/05/31 24 00
75/06/17 24 00
CP(T>-
75/06/18 24 00
75/06/29 24 00
CP(T)-
75/06/30 24 00
75/07/20 24 00
CP(T)-
75/07/21 24 00
75/07/31 24 00
CP(T>-
75/08/01 24 00
0.800
1.760
2.400
2.960
2.640
2.600
0.550
1.150
2.000
1.500
3.300
3.400
00625
TOT KJEL
N
MG/L
11.000
7.700
6.700
5.000
6.600
12.500
19.500
14.000
3.800
7.300
18.000
22.000
' P020000
37 16 20.0 093 18 45.0 4
SPRINGFIELD Nw
29 7.5 SPRINGFIELD
T/STOCKTON PES. 091491
LITTLE DKY SAC CREEK
11EPALES 0000100-*
0000 FEET OEPTn CLASS 00
00610 00671 00665 50051 50053
NH3-N PHOS-DIS PHOS-TOT FLOW CONDUIT
TOTAL ORTnO rfATE FLOw-MGD
MG/L MG/L P MG/L P INST MGD MONTHLY
0.930
0.088
5.750
2.700
0.098 1.520
1.300
3.900 7.100
3.350
2.300
7.600
7.700 8.900
1.900
0.320 2.500 3.000 5.000
0.110 2.000 2.600 3.400
0.310 4.000 5.400 2.700
5.200 4.800 5.100 1.700
2.000 6.400 6.600 1.300
1.400 3.100
3.150 5.800 6.640 1.640
1.540
3.500
2.100
1.630 2.100 5.300 2.300
2.900
3.100 3.700
2.200
2.200
1.900
1.900
2.200
1.360 2.400
1.290
-------
-.'ETRIEVvL OAT:I ' 77/02/24
DATE
FPOM
TO
00630
TIME DEPTH N02tsN03
OF N-TOTAL
DAY FEET MG/L
00
75/08/1*
CP(T)-
75/08/15 24 00
1.500
00625
TOT KJEL
N
MG/L
22.000
PO^OOOO
37 16 20.0 093 18 <*5.J
SPRINGFIELD NW
29 7.3 SPK'INGflELO
T/STUCKTON ^ES.
LITTLE CMY SAC CREEK
11EPALES 00001UO
0000 FEET DEPTH CLASS 00
091491
00610
NH3-N
TOTAL
MG/L
7.100
00671 00665
PHOS-DIS PHOS-TOT
ORTHO
MG/L P MG/L P
7.900
9.000
50051 50053
FLO* CONDUIT
RATE FLOrt-MGO
INST MGD MONTHLY
1.400
-------
STOKET ^ETrME'VAL GATE. 77/
-------
RETRIEVAL DATE 77/02/24
37 25 15.0 093 51 20.0 4
GREENFIELD Mw
T/STOCKTOfv rfES
SAC - OSAoc!
/AMSt4T/STR£AM HEPALCS
09
0000100
0000 FEET DEPTH CLASS 00
DATE
FROM
TO
75/01/17
75/02/14
75/03/17
75/04/18
75/05/08
75/05/20
75/06/04
75/07/01
75/07/21
75/08/08
75/09/29
75/10/24
75/11/14
TIME DEPTH
OF
DAY FEET
09 20
09 20
09 30
09 35
08 25
09 25
08 55
08 30
08 50
08 00
08 50
08 30
09 00
00630
N02S.N03
N-TOTAL
MG/L
1.360
1.840
0.880
0.500
0.050
0.050
0.050
0.100
0.050
0.150
0,950
0.120
0.467
00625
TOT KJEL
N
MG/L
1.300
l.OOOK
l.OOOK
1.600
1.300
3.000
2.100
4.000
3.000
6.800
4.200
6.000
3.300
00610
NH3-N
TOTAL
MG/L
0.050K
0.080K
0.100
0.081
0.050K
0.050K
0.050K
0.025K
0.050K
0.067
0.025K
0.050
0.060
00671
PHOS-DIS
ORTHO
MG/L P
0.210
0.240
0.220
0.303
0.660
0.930
0.620
0.680
0.870
0.310
0.380
0.275
00665
PHOS-TOT
MG/L P
0.360
0.280
0.299
0.730
0.380
1.200
1.700
1.200
1.300
l.bOO
0.960
0.600
0.450
50051
FLOW
RATE
INST MGD
0.034
0.073
0.013
0.019
0.019
0.013
0.013
0.013
0.075
0.013
0.013
50053
CONDUIT
FLOw-MGD
MONTHLY
0.03U
0.030
0.050
0.030
0.017
0.023
0.078
0.022
0.013
0.013
0.023
0.021
0.013
K VALUE *NOrtN TO BE
LESS THAN INDICATED
-------
OAVf t
/AMSNT/STREAV.
DATE TIME DEPTH N02&N03
FROM OF
TO DAY FEET
75/01/17
75/02/1'*
75/03/17
75/04/18
75/05/08
75/05/20
75/06/0^
75/07/01
75/07/21
75/08/08
75/09/29
75/10/24
75/11/14
09 45
09 45
10 00
09 05
09 US
09 25
08 50
09 10
08 00
09 10
08 50
09 20
P903ZA Hij£;903ZA P000350
37 24 30.0 093 50 00.0 4
GREENFIELD SE
29 7.5 GREENFIELD
T/STOCKTON RES. 091<*91
SAC - OSAGE
11EPALES 0000100-V
OCOO FEET DEPTH CLASS 00
0630
S.N03
OTAL
IG/L
'J.880
1.360
1.680
0.050
0.050
0.050
0.100
0.100
0.050
0.050
0.825
0.125
0.125
00625
TOT KJEL
N
MG/L
9.500
5.000
1.200
7.000
8.000
6.500
5.900
14.000
9.500
16.300
10.000
14.000
15.000
00610
NH3-N
TOTAL
MG/L
0.086
0.080K
0.240
0.110
0.100
0.050K
0.050K
0.125
0.050K
1.150
0.075
0.100
0.081
00671
PriOS-DIS
ORTnO
MG/L P
2.200
1.200
0.770
1.750
1.500
1.450
1.750
2.750
2.300
3*750
2.400
2.500
3.700
00665
PHOS-TOT
MG/L P
3.900
2.100
0.850
2.700
2.000
1.900
2.800
3.900
3.400
4.800
3.500
4.400
5.400
50051
FLOW
RATE
INST MGD
0.032
0.032
0.047
0.013
0.020
U.019
0.020
0.032
0.026
0.006
0.015
0.013
0.013
50053
CONDUIT
FLOrt-MGD
MONTHLY
0.010
0.010
0.030
0.025
0.020
0.003
0.020
0.032
0.027
0.013
0.019
0.021
0.013
K VALUE K.iOWN 10 3E
LESS THAN INDICATED
-------
APPENDIX E
PARAMETRIC RANKINGS OF LAKES
SAMPLED BY NES IN 1974
STATE OF MISSOURI
-------
«F (sATS ri) fit USE;;
LAKE
CODE
?901
200?
2903
2904
2905
290--
LAKE NAME
C L E A * * A T ti •> L A •< £
PriMvj OE TE^DE ^E>;EuVOIw
STOCKTON SEStKVOlK
LAKE TAN£YCOM0
THOMAS HILL ^ESEKVOIR
WAPPAPELLO RFsERVOIS
vp. n i AN
TOTAL P
0
fj
0
o
0
0
.ni7
.043
.12?
.n23
.082
.033
MEDIAN
INORG M
0. 150
n.27 =
0.670
0.531
1.040
0.105
500-
MEAN SEC
445.000
4 4 9 . 9 ? rf
42«.eoo
420.2^0
487.8^
459.667
MEAN
3.567
9.443
8.973
9.82b
5.787
9.642
M
10
14
15
11
11
11
IN 00
.400
.600
.000
.200
.200
.000
M
DISS
0.
n.
0.
u.
0.
0.
O^TnO
004
00«
006
007
Oil
004
-------
A'IT>-' j-'if>i-'
WlTi-
LAKE
CODE LAK.E
?901
2902 P0uk't ut TL«*F
2903 STOCKTON "ESF^
2904 LA> HO i .*) t>o ( 3) 100 <
t'lf 1) f^O ( 3) 40 (
------- |