U.S. ENVIRONMENTAL PROTECTION AGENCY
NATIONAL EUTROPHICATION SURVEY
WORKING PAPER SERIES
REPORT
ON
TUTTLE CREK RESERVOIR
['1ARSHALL TOTTAWATailE, AND
RILJEY COUNTIES
EPA REGION VII
WORKING PAPER No, 524
CORVALLIS ENVIRONMENTAL RESEARCH LABORATORY - CORVALLIS, OREGON
and
ENVIRONMENTAL MONITORING & SUPPORT LABORATORY - LAS VEGAS, NEVADA
•&G.P.O. 699-440
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REPORT
ON
TUITLE CREEK RESERVOIR
MARSHALL TOTTAWATOMIE, AND
RIUEY COUNTIES
MNSAS
EPA REGION VII
WORKING PAPER No, 524
WITH THE COOPERATION OF THE
KANSAS DEPARTMENT OF HEALTH AND ENVIRONMENT
AND THE
KANSAS NATIONAL GUARD
APRIL, 1977
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CONTENTS
Page
Foreword ii
List of Kansas Study Reservoirs 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 16
VI. Appendices 17
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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 freshwater 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:
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 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.
-------
111
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
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 EPA
and to augment plans implementation by the states.
ACKNOWLEDGMENT
The staff of the National Eutrophication Survey (Office of
Research & Development, U. S. Environmental Protection Agency)
expresses sincere appreciation to the Kansas State Department of
Health and Environment for professional involvement, to the Kansas
National Guard for conducting the tributary sampling phase of
the Survey, and to those Kansas wastewater treatment plant opera-
tors 'Who voluntarily provided effluent samples and flow data.
The staff of the Kansas Division of Environmental Health pro-
vided invaluable lake documentation and counsel during the Survey,
reviewed the preliminary reports, and provided critiques most use-
ful in the preparation of this Working Paper series.
Major General Edward R. Fry, the Adjutant General of Kansas,
and Project Officer Colonel Albin L. Lundquist, who directed the
volunteer efforts of the Kansas National Guardsmen, are also grate-
fully acknowledged for their assistance to the Survey.
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IV
NATIONAL EUTROPHICATION SURVEY
STUDY RESERVOIRS
STATE OF KANSAS
NAME COUNTY
'Cedar Bluff Trego
..Council Grove Morris
Elk City Montgomery
fall River Greenwood
John Redmond Coffey, Lyon
Kanopolis Ellsworth
Marion Marion
Melvern Osage
Mil ford Clay, Geary
Norton Norton
Perry Jefferson
Pomona Osage
Toronto Greenwood, Woodson
Tuttle Creek Marshall, Potta-
watomie, Riley
Wilson Russell
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TUTTLE CREEK RESERVOIR
Tributary Saripling Site
Lake Sampling Site
Sewage Treatment Facility
Land Subject to Inundation
10 20
T^ sr- ~7T~
Scale
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TUTTLE CREEK RESERVOIR
r'
Tributary Sampling Site
Lake Sampling Site
Sewage Treatment Facility
Drainage Area Boundary
Land Subject to Inundation
ip 20 3,0 *o >o Km.
10 so 30 Mi.
Scale
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TUTTLE CREEK RESERVOIR
STORET NO. 2014
I. CONCLUSIONS
A. Trophic Condition:
Survey data indicate Tuttle Creek Reservoir is potentially
eutrophic. However, the reservoir becomes quite turbid during
periods of runoff, and primary productivity is intermittently
. light-limited (Kring, 1977).
This water body ranked last in overall trophic quality
among the 15 Kansas reservoirs sampled when compared using a
combination of six water quality parameters*. All of the other
reservoirs had less median total phosphorus and dissolved ortho-
phosphorus, 11 had less and one had the same median inorganic
t
nitrogen, nine had less mean chlorophyll a^ and four had greater
mean Secchi disc transparency. Marked depression of hypolimnetic
dissolved oxygen occurred at sampling station 1 in June.
Survey limnologists did not observe concentrations of algae
or .macrophytes during sampling visits.
The low Secchi disc transparencies and numbers of phyto-
plankton indicate that at times primary productivity in the
reservoir is light-limited as noted above. In several reports
it is stated that Tuttle Creek Reservoir is eutrophic, has
high nutrient levels, but has only low to moderate productivity
due to lack of light penetration. This is generally attributed
See Appendix A.
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to the morphology of the basin and to winds which tend to*
maintain turbid conditions and also limit the time available
for photosynthesis because of vertical mixing (Klaasen and
Marzolf, 1971; Marzolf and Osborne, 1972; Osborne and Marzolf,
1972).
B. Rate-Limiting Nutrient:
Due to significant nutrient changes in the samples during
shipment, the results of the algal assays are not considered
representative of conditions in the reservoir at the times the
samples were taken. Nutrient-wise, the reservoir data indicate
nitrogen limitation in April and phosphorus limitation at two of
the three sampling stations in October.
C. Nutrient Controllability:
1. Point sources—During the sampling year, point sources
contributed only 0.7% of the total phosphorus load to Tuttle
Creek Reservoir. The wastewater treatment plants at Marysville
and Blue Rapids contributed 0.3% and 0.2% of the total load,
respectively. Eight other facilities collectively contributed
0.2%.
The present total phosphorus loading of 22.28 g/m2/year is
nearly 26 times that proposed by Vollenweider (Vollenweider'and
Dillon, 1974) as a eutrophic loading (see page 15). Removal of
phosphorus at the point sources probably would not improve the
trophic condition of the reservoir since primary productivity is
light-limited part of the time.
-------
It should be noted that if soil-conservation practices are
initiated to reduce erosion in the watershed and resulting
turbidity in the reservoir, the existing nutrient load is likely
to cause a marked increase in primary productivity. However,
it appears that a significant reduction of the phosphorus loading
can only be accomplished by control of all sources impacting
the Big Blue and Little Blue rivers (see discussion below).
2. Non-point sources--Non-point sources contributed 99.3%
of the total phosphorus load during the sampling year. The Big
Blue River contributed 60.5%, the Little Blue River contributed
33.9%, and seven other gauged tributaries collectively contributed
2.7%. The ungaged tributaries contributed an estimated 2.1% of
the total load.
The phosphorus export rates of the Big Blue and Little Blue
rivers (70 kg/km 2/year and 56 kg/km 2/year) were substantially
higher than the rates of the other gaged tributaries in the
drainage basin (see page 14). This may be due to other point
sources beyond the 40-kilometer limit of the Survey* (e.g.,
Hastings and Fairbury, Nebraska) or to land-use practices in the
drainage basin. In a recent report, it is noted that much of the
drainage is cropland, pasture, and range (Anonymous, 1975).
* See Working Paper No. 175; "...Survey Methods, 1973-1976".
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II. RESERVOIR AND DRAINAGE BASIN CHARACTERISTICS1"
ft
A. Morphometry :
1. Surface area: 63.94 kilometers2.
2. Mean depth: 8.25 meters.
3. Maximum depth: 20.0 meters.
4. Volume: 524.608 x 106 m3.
5. Eleven-year median hydraulic retention time: 139 days.
B. Tributary and Outlet:
(See Appendix C for flow data)
1. Tributaries -
Drainage Mean flow>
Name area (Jon2)* (m3/sec)*
Big Blue River 12,372.4 23.270
Otter Creek 57.0 0.188
West Fancy Creek 271.9 0.800
N. Fork Fancy Creek 93.0 0.280
Coon Creek 255.4 0.810
Little Blue River 8,609.2 18.580
Robidoux Creek 303.0 0.960
Black Vermillion River K-l 735.6 2.510
Clear Fork 115.5 0.370
Minor tributaries &
immediate drainage - 2,090.7 6.980
Totals 24,903.7 54.748
2. Outlet -
Big Blue River 24,967.6** 52.860
C. Precipitation***:
1. Year of sampling: 75.4 centimeters.
2. Mean annual: 85.1 centimeters.
t Table of metric conversions—Appendix B.
ft Kring, 1977.
* For limits of accuracy, see Working Paper No. 175.
** Includes area of reservoir.
*** See Working Paper No. 175.
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III. WATER QUALITY SUMMARY
Tuttle Creek Reservoir was sampled three times during the open-
water season of 1974 by means of a pontoon-equipped Huey helicopter.
Each time, samples for physical and chemical parameters were collected
from a number of depths at three stations on the reservoir (see map,
page v). During each visit, a single depth-integrated (4.6 m to surface)
sample was composited from the stations for phytoplankton identification
and enumeration; and during the first and last visits, 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 18.3 meters
at station 1, 10.7 meters at station 2, and 7.6 meters at station 3.
The sampling results are presented in full in Appendix D and are
summarized in the following table (the June nutrient samples were not
properly preserved and were not analyzed).
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PARAMETER
TEMP
«»«»«« _««»«««««
«««««« _««»«««««
»»««»»««
»»«««««»
»«»»«»»«
»»»«*»
tHHKHfO
»««»«»
»«»«»» -(HKHHHHHHHHHHHKHHUXUmO
««»«»« -»»»»»»«»»»»»*»»»«»«»»«
•«*«• -»*••*••*
2.8 - 14.4
0.3 - 2.3
».*..»».
7.5
1.3
oo«oo«
5.4
1.4
RANGE
15.1
7.6
473.
8.0
190.
0.083
0.056
0.700
0.030
0.400
0.760
1.300
7.5
0.2
- 17.4
6.6
- 487.
8.2
- 202.
- 0.162
- 0.067
- 0.960
- 0.070
- 1.000
- 1.010
- 1.740
- 15.8
0.6
MEAN
16.4
8.1
479.
8.1
195.
0.117
0.060
0.850
0.046
0.607
0.896
1.457
11.0
0.3
MEDIAI
16.2
8.1
477.
8.1
194.
0.111
0.058
0.845
0.045
0.550
0.880
1.440
9.7
0.2
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B. Biological characteristics:
1. Phytoplankton -
Sampling
Date
04/11/74
06/25/74
10/02/74
Dominant
Genera
1.
2.
3.
4.
5.
1.
2.
3.
4.
5.
1.
2.
3.
4.
5.
Stephanodi sens sp.
Chroomonas sp.
Cryptomonas sp.
Ankistrodesmus sp.
Nitzschia sp.
Other genera
Total
Stephanodiscus sp.
Chroomonas sp.
Melosira sp.
Cryptomonas sp.
Euglena S£.
Other genera
Total
Nitzschia sp.
Stephanodiscus sp.
Flagellates
Skeletonema sp.
Chroomonas sp.
Other genera
Total
Algal Units
per ml
10,947
2,238
241
181
60
62
13,729
1,703
183
61
30
30
76
2,083
1,641
1,452
284
189
158
95
3,819
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8
2. Chlorophyll a^ -
Sampling Station Chlorophyll a_
Date Number (ug/1)
04/11/74 1 5.1
2 6.3
3 34.5
06/25/74 1 2.8
2 14.4
3 5.4
10/02/74 1 7.5
2 9.7
3 15.8
C. Limiting Nutrient Study:
:•. The algal, assay results are not considered representative
of conditions in the reservoir at the times the samples were
taken (04/11/74 and 10/02/74) due to significant changes in
nitrogen and phosphorus during shipment from the field to the
laboratory.
The reservoir data indicate a combination of limiting
nutrients, although it will be noted that station 3 nearest
the point sources tended toward nitrogen limitation while the
two stations further away tended more toward phosphorus limi-
tation.
Following is a tabulation of the mean inorganic nitrogen/
orthophosphorus ratios for each of the sampling stations and
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times with the indicated limiting nutrient in parentheses
(however, note that primary productivity is intermittently
light-limited; Kring, 1977).
Station 04/11/74 10/02/74
1 13/1 (N?) 17/1 (P)
2 13/1 (N?) 15/1 (P)
3 10/1 (N) 12/1 (N)
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10
IV. NUTRIENT LOADINGS
(See Appendix E for data)
For the determination of nutrient loadings, the Kansas National
Guard collected monthly near-surface grab samples from each of the
tributary sites indicated on the maps (pages v and vi), except for
the months of May, June, and July when two samples were collected
at a number of the sites. Sampling was begun in October, 1974, and
was completed in September, 1975.
Through an interagency agreement, stream flow estimates for the
year of sampling and a "normalized" or average year were provided by
the Kansas District Office of the U.S. Geological Survey for the
tributary sites nearest the reservoir.
In this report, nutrient loads for sampled tributaries were
determined 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 loads for unsampled "minor tributaries and immediate
drainage" ("ZZ" of U.S.G.S.) were estimated using the means of the
nutrient loads, in kg/km 2/year, at stations C-l, D-l, E-l, and L-l
and multiplying the means by the ZZ area in km2.
The operators of the Beattie, Blue Rapids, Frankfort, Marysville,
Randolph, and Watersville wastewater treatment plants provided monthly
effluent samples and corresponding flow data. The operators of the
* See Working Paper No. 175.
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11
wastewater treatment plants at Axtell, Greenleaf, Hanover, and Washington
also provided monthly samples, but corresponding flow data were not
available. Nutrient loads from these sources were estimated at 1.134
kg P and 3.401 kg N/capita/year, and flows were estimated at 0.3785
m3/capita/day.
A. Waste Sources:
1. Known municipal* -
Name
Axtel 1
Beattie
Blue Rapids
Frankfort
Greenleaf
Hanover
Marysville
Randol ph
Washington
Water ville
Pop.
Served
514
296
1,298
1,060
485
838
3,740
145
1,700
750
Mean Flow
Treatment (m3/d)
tr. filter 194.5
stab, pond 106.0
prim, clari- 649.2
fier
stab, pond 772.5
tr. filter 183.6
prim, clari- 317.2
fier
prim, clari- 1,309.8
fier
act. sludge 32.6
tr. filter 643.5
prim, clari- 258.9
fier
Receiving
Water
Vermill ion
River
Trib. of Robi-
doux Creek
Big Blue River
Black Ver-
mill ion River
Coon Creek
Little Blue
Ri ver
Big Blue
Ri ver
Peach Creek
Peach Creek
Little Blue
River
2. Industrial - Unknown
* Treatment plant questionnaires.
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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) -
Big Blue River 861,300 60.5
Otter Creek 735 <0.1
West Fancy Creek 3,950 0.3
N. Fork Fancy Creek 1,410 0.1
Coon Creek 3,560 0.3
Little Blue River 482,715 33.9
Robidoux Creek 8,655 0.7
Black Vermillion River K-l 16,785 1.2
Clear Fork 1,310 0.1
b. Minor tributaries & immediate
drainage (non-point load) - 29,895 2.1
c. Known municipal STP's -
Axtell 585 <0.1
Beattie 310 <0.1
Blue Rapids 2,555 0.2
Frankfort 1,050 <0.1
Greenleaf 550 <0.1
Hanover 950 0.1
Marysville 3,975 0.3
Randolph 100 <0.1
Washington 1,930 0.1
Waterville 865 <0.1
d. Septic tanks - Unknown ?
e. Industrial - Unknown ?
f. Direct precipitation* - 1.120 0.1
Total 1,424,305 100.0
2. Outputs -
Lake outlet - Big Blue River 229,125
3. Net annual P accumulation - 1,195,180 kg.
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) -
Big Blue River 4,282,460 55.3
Otter Creek 10,355 0.1
West Fancy Creek 72,290 1.0
N. Fork Fancy Creek 23,170 0.3
Coon Creek 223,550 2.9
Little Blue River 2,159,265 28.0
Robidoux Creek 121,720 1.6
Black Vermillion River K-l 212,200 2.8
Clear Fork 23,580 0.3
b. Minor tributaries & immediate
drainage (non-point load) - 485,670 6.3
c. Known municipal STP's -
Axtell 1,750 <0.1
Beattie 920 <0.1
Blue Rapids 9,065 0.1
Frankfort 3,525 <0.1
Greenleaf 1,650 <0.1
Hanover 2,850 <0.1
Marysville 13,450 0.2
Randolph 370 <0.1
Washington 5,780 0.1
Waterville 3,860 0.1
d. Septic tanks - Unknown ? -
e. Industrial - Unknown ?
f. Direct precipitation* - 69.030 0.9
Total 7,726,510 100.0
2. Outputs -
Lake outlet - Big Blue River 4,192,595
3. Net annual N accumulation - 3,533,915 kg.
* See Working Paper No. 175.
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14
D. Non-point Nutrient Export by Subdrainage Area:
Tributary kg P/km2/yr kg N/km2/yr
Big Blue River 70 346
Otter Creek 13 182
West Fancy Creek 15 266
N. Fork Fancy Creek 15 249
Coon Creek 14 875
Little Blue River 56 251
Robidoux Creek 29 402
Black Vermillion River 23 288
Clear Fork 11 204
E. Mean Nutrient Concentrations in Ungaged Streams:
Mean Total P Mean Total N
Tributary Cone, (mg/1) Cone, (mg/1)
Mclntire Creek 0.075 2.548
Corndodger Creek 0.067 1.883
Cedar Creek 0.040 0.868
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15
F. Yearly Loads:
In the following table, the existing phosphorus loadings
are compared to those proposed by Vollenweider (Vollenweider
and Dillon, 1974). Essentially, his "dangerous" loading is
one at which the receiving water would become eutrophic or
remain eutrophic; his "permissible" loading is that which
would result in the receiving water remaining oligotrophic
or becoming oligotrophic if morphometry permitted. A meso-
trophic loading 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.
Jotal Phosphorus Total Nitrogen
Total Accumulated Total Accumulated
grams/m2/yr 22.28 18.70 120.8 55.3
Vollenweider phosphorus loadings
(g/m2/yr) based on mean depth and 11-year median
hydraulic retention time of Tuttle Creek Reservoir:
"Dangerous" (eutrophic loading) 0.86
"Permissible" (oligotrophic loading) 0.43
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16
V. LITERATURE REVIEWED
Anonymous, 1975. Draft environmental statement: Operation and
maintenance - Tuttle Creek Reservoir, Kansas. Kansas City
Distr., Corp. of Engrs., Kansas City, MO.
Klaassen, Harold E., and G. Richard Marzolf, 1971. Relationships
between distributions of benthic insects and bottom-feeding
fishes in Tuttle Creek Reservoir. Reservoir Fisheries &
Limnology, Special Pub!. No. 8, Amer. Fish. Soc.
Kring, R. Lynn, 1977. Personal communication (revised reservoir
morphemetry; primary productivity). KS Dept. of Health &
Environment, Topeka.
Marzolf, G. R., and John A. Osborne, 1972. Primary production
in a Great Plains reservoir. Verh. Internat. Verein. Limnol.
18; 126-133
Osborne, John A., and G. Richard Marzolf, 1972. Effect of spectral
composition on photosynthesis in turbid reservoirs. Water
Resources Res. Inst., KS St. U., Manhattan.
Schwartz, Joseph M., and G. R. Marzolf, 1972. Sediment characteristics
and distribution in Tuttle Creek Reservoir, Kansas. Trans. KS
Acad. of Sci. 74(1).
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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17
VI. APPENDICES
APPENDIX A
LAKE RANKINGS
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LAKE
LAKE
CODE
2001
2002
2003
2004
2005
2006
2007
2008
2009
2010
2011
2012
2013
2014
2015
LAKE NAME
CEDAR BLUF
COUNCIL GROVE
ELK CITY
FALL RIVER
JOHN REDMC
KANOPOLIS
MARION RESERVOIR
MELVERN RESERVOI
MILFORD RESERVOI
NORTON RESERVOIR
PERRY RESERVOIR
POMONA RESERVOIR
TORONTO RESERVOI
TUTTLE CREEK RES
WILSON RESERVOIR
:o IN RANKINGS
MEDIAN
TOTAL P
IESERVOIR 0.017
I 0.069
0.030
iSERVOIR 0.053
RESERVOIR 0.118
;ERVOIR o.os6
'OIR 0.052
tVOlR , 0.034
tVOIR 0.079
'OIR 0.122
)IR 0.055
'OIR 0.040
iVOIR 0.067
RESERVOIR 0.162
'OIR 0.023
MEDIAN
INORG N
0.055
0.830
0.590
0.470
1.250
0.640
0.430
0.265
0.710
0.110
0.970
1.240
0.425
0.970
0.265
500-
MEAN SEC
431.667
485.889
490.400
488.667
492.667
487.000
483.667
459.111
466.333
476.750
478.571
481.333
488.500
470.667
445.222
MEAN
CHLORA
4.217
9.789
3.212
7.683
9.467
16.033
12.400
30.400
18.883
21.360
5.614
8.312
6.583
11.278
8.867
15-
MIN DO
10.800
10.400
14.000
9.200
8.200
10.200
9.000
14.400
12.800
8.000
13.400
13.000
13.000
13.600
13.400
MEDIAN
DISS ORTHO P
0.004
0.028
0.003
0.016
0.066
0.011
0.010'
0.007
0.036
0.036
0.017
0.021
0.011
0.067
0.004
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LAKES RANKED 3Y INDEX NOS.
RANK LAKE CODE LAKE NAME INDEX NO
1 2001 CEDAR BLUFF RESERVOIR 539
2 2015 WILSON RESERVOIR 439
3 2007 MARION RESERVOIR 357
4 2003 ELK CITY 350
5 2004 FALL RIVER RESERVOIR 328
6 2008 MELVERN RESERVOIR 326
7 2013 TORONTO RESERVOIR 303
8 2010 NORTON RESERVOIR 292
9 2011 PERRY RESERVOIR 279.
10 2006 KANOPOLIS RESERVOIR 271
11 2012 POMONA RESERVOIR 267
12 2002 COUNCIL GROVE 230
13 2009 MILFORD RESERVOIR 214
14 2005 JOHN REDMOND RESERVOIR 164
15 2014 TUTTLE CREEK RESERVOIR 139
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PERCENT OF LAKES WITH HIGHER VALUES (NUMBER OF LAKES WITH HIGHER VALUES)
LAKE
CODE LAKE NAME
2001 CEDAR BLUFF RESERVOIR
2002 COUNCIL GROVE
2003 ELK CITY
2004 FALL RIVER RESERVOIR
2005 JOHN REDMOND RESERVOIR
2006 KANOPOLIS RESERVOIR
2007 MARION RESERVOIR
2008 MELVERN RESERVOIR
2009 MILFORD RESERVOIR
2010 NORTON RESERVOIR
2011 PERRY RESERVOIR
2012 POMONA RESERVOIR
2013 TORONTO RESERVOIR
2014 TUTTLE CREEK RESERVOIR
2015 WILSON RESERVOIR
MEDIAN
TOTAL P
100 (
29 (
86 <
57 (
14 (
43 (
64 (
79 (
21 <
7 (
50 (
71 (
36 (
0 (
93 (
14)
4)
12)
8)
2>
6)
9)
11)
3)
1)
7)
10)
5)
0)
13)
MEDIAN
INORG N
100 1
29 1
50 1
57 1
0 1
43 1
64 1
82 <
36 <
93 1
18 <
7 1
71 1
18 <
82 1
I 14)
! 4)
[ 7)
[ 8)
t 0)
[ 6)
[ 9)
[ 11)
I 5)
I 13)
: 2)
! 1)
[ 10)
t 2)
I 11)
500-
MEAN SEC
100 I
36 1
7 1
14 1
0 1
29 (
43 1
86 1
79 1
64 1
57 (
50 1
21 1
71 1
93 <
[ 14).
: 5)
[ i)
: 2)
: o)
: 4)
: 6)
: 12)
: ii)
: 9)
: 8>
; 7)
[ 3)
: 10)
I 13)
MEAN
CHLORA
93 (
43 (
100 (
71 (
50 (
21 (
29 (
0 (
14 (
7 <
86 (
64 (
79 (
36 (
57 (
13)
6)
14)
10)
7)
3)
4)
0)
2)
1)
12)
9)
11)
5)
8)
15-
MIN DO
57 1
64 (
7 (
79 (
93 (
71 (
86 1
0 <
50 (
100 (
25 <
39 1
39 1
14 1
25 1
! 8)
: 9>
: i)
: ID
: 13)
: 10)
: 12)
: o>
; 7)
: 14)
: 3)
: 5)
: 5)
I 2)
I 3)
MEDIAN
DISS OftThO P
. 89 1
29 1
100 1
50 I
7 1
64 1
71 I
79 I
14 1
21 i
43 1
36 i
57 i
0 i
89 i
: i-2)
: 4)
[ 14)
! 7)
1 1)
I 9)
1 10)
t 11)
[ 2)
( 3)
[ 6)
( 5)
( 8)
( 0)
( 12)
INDEX
NO
539
230
350
328
164
271
' 357
326
214
292
279
267
303
139
439
-------
APPENDIX B
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"4 = acre/feet
Square kilometers x 0.3861 = square miles
Cubic meters/sec x 35.315 = cubic feet/sec
Centimeters x 0.3937 = inches
«
Kilograms x 2.205 = pounds
Kilograms/square kilometer x 5.711 = Ibs/square mile
-------
APPENDIX C
TRIBUTARY FLOW DATA
-------
TRIBUTARY FLOW INFORMATION POP KANSAS
LAKE CODE 2014 TuTTLE CREEK
TOTAL DRAINAGE AREA OF LAKE(SO KM) 24936.5
05/03/76
SUB-DRAINAGE
TRIBUTARY A&EAISQ KM)
JAN
FE8
MAR
APR
MAY
NORMALIZED FLOWS(CMS)
JUN JUL AUG
SEP
OCT
NUV
DEC
SUMMARY
TOTAL DRAINAGE AREA OF LAKE = 24936.5
SUM OF SUB-DRAINAGE AREAS = 25672.1
TOTAL FLOW IN = 703.91
TOTAL FLOW OUT = 634.01
MEAN MONTHLY FLOWS AND DAILY FLOWS(CMS)
TRIBUTARY MONTH YEAR
2C14A1
MEAN FLOW DAY
FLOW DAY
FLOW DAY
FLOW
2014A2
10
11
12
1
2
3
4
5
6
7
a
9
10
11
12
1
2
3
4
5
6
7
8
9
74
74
74
75
75
75
75
75
75
75
75
75
74
74
74
75
75
75
75
75
75
75
75
75
13.904
32.423
12.063
5.918
0.620
1.863
108.737
33.244
178.113
142.972
28.883
7.391
6.371
5.267
4.248
7.164
6.31S
27.156
12.459
25.315
75.889
17.755
6.400
4.304
12
9
14
11
11
8
15
5
14
17
10
13
13
10
15
12
9
9
'13
24
14
11
10
14
8.438
27.354
14.300
1.388
0.453
0.249
234.180
54.935 24
145.265 28
64.562 22
20.785
5.663
2.775
2.832
3.313
5.210
3.625
15.065
10.874
5.663
48.139 28
9.911 13
3.766
3.228
2.322
152.345
14.442
110.436
3.341
MEAN
2014A1
201<*A2
2014C1
2014D1
2014E1
2014F1
2014G1
201<«J1
2014K1
2014K2
2014L1
2014ZZ
24967.6
12372.4
57.0
271.9
93.0
255.4
8609.2
303.0
735.6
1061.9
115.5
1797.2
20.3-i
8.7d
0.082
0.34
0.12
0.34
10.19
0.40
1.02
1.90
C.16
2.66
42.^8
13.41
0.108
0.45
0.16
0.45
16.14
0.54
1.44
4.25
0.21
3.68
84.95
36.81
0.272
0.96
0.37
1.02
27.47
1.19
2.30
5.10
0.51
6.51
62.30
22.09
0.227
0.99
0.34
1.02
15.86
1.22
3.40
3.11
0.45
8.50
82.12
31.15
0.340
1.43
0.51
1.44
31.15
1.70
4.25
6.80
0.68
11.89
96.28
65.13
0.311
1.56
0.48
1.56
31.15
1.84
5.10
7.93
0.65
14.72
70.79
31.15
0.368
1.47
0.54
1.47
18.12
1.73
4.25
4.25
0.71
11.33
36.81
20.10
0.105
0.51
0.16
0.51
11.33
0.62
1.67
1.67
0.22
5.95
39.64
20.95
0.119
0.59
0.18
0.59
22.09
0.71
2.01
4.81
0.25
6.80
39.64
12.18
0.156
0.65
0.23
0.65
24.07
0.79
1.98
4.53
0.31
5.66
33.98
7.08
0.071
0.31
0.10
0.34
9.06
0.40
1.13
1.50
0.15
3.40
24.64
5.66
0.085
0.31
0.12
0.34
6.23
0.40
0.96
1.19
0.16
2.58
52.86
23.27
0.188
0.80
0.28
0.81
18.58
0.96
2.51
3.91
0.37
6.98
-------
TRIBUTARY FLOW INFORMATION FOR KANSAS
05/03/76
LAKE CODE 2014
TUTTLE. CREEK
MEAN MONTHLY FLOWS AND DAILY FLOwS(CMS)
201<*C1
201401
2014E1
2014F1
MONTH YEAR
10
11
12
1
2
3
4
5
6
7
B
9
10
11
12
1
2
3
4
5
6
7
8
9
10
11
12
1
2
3
4
5
6
7
8
9
10
11
12
1
2
3
4
5
6
7
8
9
74
74
74
75
75
75
75
75
75
75
75
75
74
74
74
75
75
75
75
75
75
75
75
75
74
74
74
75
75
75
75
75
75
75
75
75
74
74
74
75
75
75
75
75
75
75
75
75
MEAN FLO* fiAY
0.034
0.037
0.042
0.054
0.076
0.283
0.278
0.232
0.793
0.113
0.027
0.008
0.142
0.161
0.153
0.224
0.340
0.991
1.218
0.963
3.964
0.453
0.130
0.040
0.051
0.054
0.059
0.079
0.113
0.396
0.4?5
0.340
1.218
0.164
0.042
0.012
0.142
0.178
0.167
0.224
0.340
1.048
1.246
0.991
3.964
0;453
0.130
0.040
12
9
14
10
8
8
5
5
14
17
10
13
12
9
14
10
8
8
5
5
14
17
10
12
12
9
14
11
8
e
5
5
14
17
10
13
13
10
15
9
9
13
18
14
13
10
14
FLO* OAT-
DAY
FLOW
0.004
0.017
0.003
0.003
0.025
0.034
0.878
0.071
0.187
0.105
0.059
0.014
0.212
0.283
0.184
0.0
0.275
0.255
0.566
0.425
0.510
0.142
0.142
0.164
0.119
0.170
0.099
0.091
0.127
0.119
0.232
0.142
0.266
0.142
0.071
0.099
0.241
0.311
0.269
0.311
0.311
0.340
0.193
0.453
0.2S5
0.311
0. 196
27
28
22
27
28
22
27
28
22
29
27
3.964
0.176
0.0b9
2.549
0.595
0.170
0.708
0.241
0.142
0.425
0.425
-------
FLOW INFORMATION FOR KANSAS
OS/03/76
LAKE COOE 2014
TUTTLE CREEK
MEAN MONTHLY FLOWS AND DAILY FLOWS(CMS)
TRIBUTARY MONTI YEAK
MEAN FLOW DAY
FLOw DAY
FLOW DAY
FLOW
2014G1
2014J1
2014K1
2014K2
10
11
12
1
2
3
4
5
6
7
8
9
10
11
12
1
2
3
4
5
6
7
8
9
10
11
12
1
2
3
it
5
6
7
8
9
10
11
12
1
2
3
4
5
6
7
8
9
74
74
74
75
75
75
75
75
75
75
75
75
74
74
74
75
75
75
75
75
75
75
75
75
74
74
74
75
75
75
75
75
75
75
75
75
74
74
74
75
75
75
75
75
75
75
75
75
3.625
4.955
4.786
5.352
5.663
30.016
12.290
13.989
76.172
39.927
12.176
4.474
0.173
0.207
0.195
0.261
0.396
1.246
1.501
1.161
4.531
0.538
0.159
0.045
0.425
0.595
0.481
0.660
1.048
2.832
4.248
2.832
12.743
1.303
0.425
0.130
0.968
0.779
0.578
1.237
3.143
5.324
3.766
4.559
20.105
1 . 294
0.425
0.314
13
10
15
12
9
9
13
18
14
13
10
14
13
10
15
12
9
9
13
18
14
12
9
14
13
10
15
12
9
9
13
18
14
12
9
14
13
10
15
12
9
9
13
18
14
12
9
14
3.596
5.295
5.295
4.531
4.248
14.951
10.534
6.853
30.299 29
12.544 27
11.242
3.823
0.071
0.170
0.142
0.057
0.283
0.481
0.396
0.255
1.104 29
0.311 29
0.085
0.113
0.085
1.416
0.283
0.283
0.991
1.133
1.133
0.368
1.756 29
1.274 29
0.144
0.538
0.142
2.718
0.623
0.510
1.557
1.962
1.359
0.708
3.936 29
1.104 29
0.269
0.249
36.812
59.749
1.331
0.127
1.982
0.765
2.945
0.453
-------
TRIBUTARY FLO* INFORMATION
KANSAS
05/03/76
LA
-------
APPENDIX D
PHYSICAL and CHEMICAL DATA
-------
STORE, RETRIEVAL DATE 76/05/03
DATE TIME DEPTH
FROM OF
TO DAY FEET
74/04/11 12 15 0000
12 15 0005
12 15 0015
12 15 0030
12 15 0060
74/06/25 14 00 0000
14 00 0005
14 00 0015
14 00 0030
14 00 0040
14 00 0050
14 00 0060
74/10/02 15 35 0000
15 35 0005
15 35 0015
15 35 0030
15 35 0045
15 35 0060
DATE TIME DEPTH
FROM OF
TO DAY FEET
74/04/11 1? 15 0000
12 15 0005
12 15 0015
12 15 0030
12 15 0060
74/06/25 14 00 0000
74/10/02 15 35 0000
15 35 0005
15 35 0015
15 35 0030
15 35 0045
15 35 0060
00010
WATER
TEMP
CENT
9.4
9.3
9.3
9.2
9.2
25.4
24.8
23.4
22.9
22.4
21.7
21.4
17.4
17.3
17.4
17.3
17.3
17.3
00665
PHOS-TOT
MG/L P
0.190
0.182
0.181
0.181
0.170
0.083
0.086
0.085
0.084
0.085
0.095
00300 00077 00094
00 TRANSP CNDUCTVY
SECCHI FIELD
MG/L INCHES MICHOMHO
28
9.8
10.4
10.2
10.2
8.0 90
7.6
7.0
5.2
3.8
2.6
1.4
8.0 24
8.0
7.6
8.0
7.6
7.8
32217 00031
CHLRPHYL INCDT LT
A REMNING
UG/L PERCENT
5.1
2.8
7.5
1.0
395
394
393
394
404
557
544
531
534
532
531
^"14
JO*t
475
475
475
475
477
479
201401
39 15 19.0 096 36 11.0 3
TUTTLE CREEK RESERVOIR
20161 KANSAS
091191
11EPALES
0065 FEET
2111202
DEPTH CLASS 00
su
6.20
8.10
8.10
6.10
8.10
8.60
8.4C
8.30
8.40
8.40
8.10
8.10
8.07
8.13
8.13
8.13
8.09
8.05
T
T ALK
CAC03
MG/>-
200
199
197
196
198
196
190
190
192
190
191
00610
NH3-N
TOTAL
MG/L
0.160
0.150
0.160
0.150
0.150
0.050
0.030
0.030
0.040
0.050
0.050
00625
TOT KJEL
N
MG/L
0.600
0.400
0.400
0.400
0.400
0.500
0.500
0.500
0.400
0.500
0.500
N02&N03
N-TOTAL
MG/L
1.880
1.580
1.630
1.750
1.870
00671
PHOS-LtIS
ORTHO
MG/L P
0.154
0.152
0.149
0.148
0.139
0.960
0.940
0.940
0.950
0.960
0.960
0.059
0.058
0.059
0.058
0.058
0.056
-------
S10RET RETRIEVAL DATE 76/05/03
201403
39 18 41.0 096 39 06.0 3
TUTTUE CREEK RESERVOIR
20149 KANSAS
091191
HEPALES 2111202
0035 FEET DEPTH CLASS 00
00010
WATER
TEMP
CENT
9.5
9.5
9.4
9.4
24.9
24.1
23.5
22.7
22.1
16.2
16.2
16.1
16.0
00300
00
MG/L
10.6
10.2
10.4
9.2
e.4
6.6
5.2
3.2
8.4
8.4
8.4
8.2
00077
TRANSP
SECCHI
INCHES
25
54
9
00094
CNOUCTVY
FIELD
MICROMMO
394
394
394
396
537
524
523
526
526
473
477
477
475
00400
PH
SU
8.15
8.15
8.15
8.20
8.4Q
8.4C
8.60
8.40
8.00
8.15
8.19
8.19
8.11
00410
T ALK
CAC03
MG/L
201
195
195
198
191
194
194
196
00610
NH3-N
TOTAL
MG/L
0.150
0.150
0.160
0.150
0.030
0.030
0.040
0.040
00625
TOT KJEL
N
MG/L
0.600
0.400
0.300
0.300
0.500
0.600
0.600
0.900
00630
N02&N03
N-TOTAL
MG/L
1.840
1.690
1.830
1.840
0.850
0.820
0.840
0.820
00671
HHOS-OIS
ORTHO
MG/L P
0.153
0.154
0.155
0.151
0.059
0.057
0.057
0.058
DATE
FROM
TO
74/04/11
74/06/25
74/10/02
00665 32217 00031
TIME DEPTH PHOS-TOT CHLRPHYL INCDT LT
OF A REMNING
DAY FEET
12 45 0000
12 45 0005
12 45 0015
12 45 0030
14 JO 0000
15 00 0000
15 00 0003
15 00 0005
15 00 0015
15 00 0028
MG/L P UG/L PERCENT
0.197 6.3
0.190
0.189
0.191
14.4
0.110 9.7
1.0
0.113
0.121
0.146
-------
STORET RETFflEVtL DATE 76/05/03
201403
39 26 00.0 096 42 50.0 3
TUTTLE CREEK RESERVOIR
26161 KANSAS
091191
11EPALES 2111202
0027 FEET DEPTH CLASS 00
DATE
FROM
TO
74/04/11
74/06/25
74/10/02
DATE
FROM
TO
74/04/11
74/06/25
74/10/02
TIME DEPTH
OF
DAY FEET
13
13
13
13
15
15
15
15
14
14
14
14
10
10
10
10
05
05
05
05
30
30
30
30
0000
0005
0015
0022
0000
0005
0015
0025
0000
0005
0015
0021
00010
WATER
TEMP
CENT
11.3
11.3
11.4
11.4
24.7
24.1
24.0
23.9
15.5
15.3
15.1
15.1
00665
TIME DEPTH
OF
DAf
13
13
13
13
15
14
14
14
14
14
FEET
10
10
10
10
05
30
30
30
30
30
0000
0005
0015
0022
0000
0000
0002
0005
0015
0021
PHOS-TOT
MG/L P
0
0
0
0
0
0
0
0
.246
.229
.235
.249
.155
.159
.162
.161
00300
DO
MG/L
9.
9.
9.
6.
6.
6.
5.
8.
a.
8.
8.
32217
00077 00094
TRANSP CNDUCTVY
SECCHI FIELD
INCHES MICROMHO
15
8
4
4
2 12
0
0
6
6 7
4
2
0
00011
513
511
516
518
507
637
696
792
487
485
485
487
00400 00410 00610 00625 00630 00671
PH T ALK NH3-N TOT KJEL N02&N03 PhOS-DIS
CAC03 TOTAL N N-TOTAL ORTrlO
SU
8.
8.
8.
8.
8.
8.
8.
8.
8.
8.
8.
8.
30
25
25
25
2C
40
20
10
17
17
17
13
MG/L MG/L MG/L MG/L MG/L P
264 0.130 0.800 0.720 0.083
252 0.150 0.600 0.770 0.087
264 0.110 0.600 0.660 0.086
264 0.120 0.500 0.660 0.089
202 0.070 1.000 0.740 0.067
202 0.060 0.700 0.720 0.063
202 0.060 0.700 0.700 0.064
202 0.060 0.600 0.700 0.062
CHLRPHYL INCDT LT
A
UG/L
REMNING
PERCENT
34.5
5 ,
i
Is'.B
1.0
-------
APPENDIX E
TRIBUTARY AND WASTEWATER
TREATMENT PLANT DATA
-------
STORET RETRIEVAL OAT£ 7(S/05/04
DATE TIME
FROM OF
TO DAY FEET
74/10/12
74/11/09
74/12/14
75/01/11
75/04/15
75/05/05
75/05/34
75/06/14
75/06/28
75/07/17
75/07/22
75/08/10
75/09/13
09 ?5
09 55
09 50
10 00
11 00
10 05
10 45
09 55
10 00
12 50
09 50
15 15
17 05
10 45
2014A1
39 15 09.0 096 36 01.0 4
616 6LUE RIVER
20 7.5 TUTTLE CR DM
0/TUTTLE CREEK RESERVOIR 091191
BANK SAMP AT SE BASE OF TUTTLE CREEK DAM
11EPALES 2111204
0000 FEET DEPTH CLASS 00
00630
N02&N03
N-TOTAL
MG/L
0.860
0.780
0.704
0.480
0.575
0.870
0.910
.600
.720
.650
.650
.800
0.090
1.570
00625
TOT KJEL
N
MG/L
1.300
1.000
0.700
2.300
1.700
1.300
1.400
0.700
0.850
0.900
0.700
1.050
1.400
1.000
00610
NH3-N
TOTAL
MG/L
0.032
0.050
0.025
0.088
0.139
0.145
0.240
0.025
0.015
0.010
0.005
0.020
0.025
0.030
00671
PHOS-DIS
ORTHO
MG/L P
0.060
0.050
0.050
0.020
0.030
0.060
0.075
0.100
0.120
0.130
0.145
0.150
0.070
0.160
00665
PHOS-TOT
MG/L P
0.095
0.080
0.070
0.060
0.080
0.120
0. 140
0.160
0.190
0.210
0.230
0.230
0.150
0.200
-------
STORET RETRIEVAL DATE 76/05/04
2014A2
39 50 32.0 096 39 40.0 4
BIG tfLUE RIVER
20 7.5 MARYSVILLE
T/TUTTLE CREEK RESERVOIR 091191
US HWY 36 BRDG AT w EDGE OF MARYSVILLE
11EPALES 2111204
0000 FEET DEPTH CLASS 00
DATE
FROM
TO
74/10/13
74/11/10
74/12/15
75/01/12
75/02/09
75/03/09
75/04/13
75/05/24
75/06/14
75/06/28
75/07/11
75/07/13
75/08/10
75/09/14
00630 00625
TIME DEPTH N026.N03 TOT KJEL
OF N-TOTAL N
DAY FEET MG/L
08
09
13
14
13
13
13
10
10
13
13
13
15
14
SO
30
10
10
40
15
40
50
50
55
10
35
55
00
0
1
1
1
2
1
2
1
2
1
2
1
2
1
.016
.120
.760
.680
.000
.780
.100
.800
.900
.650
.800
.450
.200
.650
MG/L
1.
2.
0.
3.
2.
2.
1.
1.
5.
4.
2.
1.
2.
1.
200
300
800
300
300
100
800
700
600
200
200
100
500
200
00610 00671 00665
NH3-N PMOS-DIS PHOS-TOT
TOTAL ORTHO
MG/L
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
060
260
090
336
304
472
360
035
095
045
103
015
030
015
MG/L
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
P
310
370
380
300
384
440
375
315
345
425
430
460
400
MG/L P
0.500
0.460
0.460
0.400
0.500
0.630
0.540
1.900
1.750
0.805
0.560
0.600
0.600
-------
STORET RETRIEVAL DATE 76/05/04
DATE TIME DEPTH N02&N03
FROM OF
TO DAY FEET
74/10/12
74/11/09
74/12/14
75/01/11
75/02/08
75/03/08
75/04/05
75/05/05
75/05/27
75/06/14
75/06/28
75/07/17
75/07/22
75/08/10
75/09/13
12 48
09 40
09 35
09 45
09 45
15 45
09 43
10 10
14 00
10 00
09 35
12 20
09 35
15 10
09 35
39 19 30.0 096 45 00.0 4
MILL CREEK
20 RILEY CO h«Y MAP
T/TUTTLE CREEK RESERVOIR 091191
H*Y 7T BRDG 7 MI S OF RANDOLPH
11EPALES 2111204
0000 FEET DEPTH CLASS 00
10630
I&N03
OTAL
IG/L
0.224
0.690
0.504
0.760
1.350
1.035
0.175
0.525
0.500
1.900
1.880
0.945
0.770
0.420
0.670
00625
TOT KJEL
N
MG/L
2.700
2.500
1.250
2.000
1.900
1.500
0.550
1.550
0.900
0.800
0.700
0.600
0.700
0.500
0.500
00610
NH3-N
TOTAL
MG/L
0.060
0.085
0.090
0.352
0.432
0.040
0.030
0.170
0.085
0.050
0.030
0.040
0.060
0.035
O.G30
00671
PHOS-DIS
ORTHO
MG/L P
0.020
0.230
0.015
0.060
0.152
0.044
0.020
0.070
0.110
0.120
0.030
0.035
0.010
0.020
0.050
00665
PHOS-TOT
MG/L P
0.090
0.290
0.035
0.160
0.220
0.070
0.090
0.140
0.170
0.205
0.130
0.060
0.060
0.070
0.100
-------
STORE! RETRIEVAL DATE 76/05/04
2014C1
39 27 55.0 096 51 15.0 4
OTTER CRtEK
20 7.5 RANDOLPH
T/TUTTLE CREEK REStRvOIR 0911*1
SEC *0 8*DG 4.3 MI ESE OF MAr DAY
IIE^ALES 2111204
0000 FEET DEPTH CLASS 00
DATE
FROM
TO
74/10/12
74/11/09
74/12/14
75/03/08
75/04/05
75/05/05
75/05/27
75/06/14
75/06/28
75/07/17
75/07/22
75/08/10
75/09/13
TIME DEPTH
OF
DAY FEET
12 20
10 15
10 05
09 40
10 20
10 40
14 35
10 30
10 10
12 45
10 00
15 30
10 00
00630
N02&N03
N-TOTAL
MG/L
0.024
0.232
0.152
0.815
0.185
0.145
0.170
1.000
1.000
0.740
0.830
0.735
0.890
00625
TOT KJEL
N
MG/L
C
C
1
G
1
1.200
1.000
.100
.400
.550
.750
.200
.250
1.400
1.300
.400
.600
.300
00610
NH3-N
TOTAL
MG/L
0.025
0.045
0.020
0.044
0.030
0.100
0.055
0.060
0.025
0.020
0.045
0.070
0.060
00671
PHOS-DIS
ORTMO
MG/L P
0.020
0.040
0.025
0.048
0.035
0.045
0.025
0.100
0.015
0.035
0.005
0.030
0.050
00665
PHOS-TOT
MG/L P
0.080
0.040
0.040
0.100
0.100
0.090
0.190
0.250
0.100
0.050
0.160
0.090
0.090
-------
WEifilEVAI. DATE 76/05/04
DATE TIME DEPTH
FROM OF
TO DAY FEET
74/10/12 12 02
74/11/09 10 45
74/12/14 10 25
75/03/08 10 40
75/03/08 09 30
75/04/05 10 30
75/05/05 11 07
75/05/27 15 00
75/06/14 11 00
75/06/28 10 30
75/07/17 13 00
75/07/22 16 ?5
75/08/10 15 45
75/09/12 10 15
00630
N02&N03
N-TOTAL
MG/L
OCA A
• Dv**
1.200
1.440
1.600
1.935
1.570
0.575
0.450
1.900
1.570
0.200
0.145
0.360
0.840
00625
TOT KJEL
N
MG/L
3.130
1.700
0.900
2.500
2.900
2.400
1.200
0.950
2.200
0.850
1.100
1.350
1.000
1 t^rt A
I • jUw
00610
NH3-N
TOTAL
MG/L
0.360
0.085
0.025
0.480
0.464
0.145
0.030
0.035
0.100
0.045
0.045
0.020
0.030
0.120
00671
PHOS-OIS
ORTHO
MG/L P
0.010
0.080
0.015
0.120
0.128
0.210
O.OSO
0.025
0.115
0.050
0.020
0.015
0.020
0.075
00665
PHOS-TOT
MG/L P
0.130
0.110
0.040
0.260
0.185
0.230
0.120
0.150
0.325
0.190
0.120
0.130
0.140
0.160
201401
39 29 05.0 096 54 47.0 4
WEST FANCY CREEK
20 7.5 LASITA
T/TUTTLE CREEK RESERVOIR 091191
SEC «D 8RDG .6 Ml S OF MAY DAY
11EPALES 2111204
0000 FEET DEPTH CLASS 00
-------
STORET RETRIEVAL DATE 76/05/04
DATE TIME DEPTH
FROM OF
TO DAY FEET
74/10/12
74/11/09
74/13/14
75/01/11
75/02/08
75/03/08
75/04/05
75/05/05
75/05/27
75/06/14
75/06/28
75/07/17
75/07/22
75/08/10
75/09/13
12 05
10 30
10 15
10 45
10 30
09 20
10 30
10 55
15 15
10 45
10 21
12 55
10 20
13 37
10 10
2014E1
39 29 29.0 096 53 05.0 4
N FORK FANCY CREEK
20 7.5 LASITA
T/TUTTUE CREEK RESERVOIR 091191
UNIMPROVED *D 8RDG 1.8 MI £ OF MAY DAY
11EPALES 2111204
0000 FEET DEPTH CLASS 00
)0630
?&N03
FOTAL
4G/L
0.240
1.000
i.oao
0.960
1.720
1 .935
1.350
0.710
0.840
2.500
2.300
1.350
1.050
0.570
1.500
00625
TOT KJEL
N
MG/L
1.900
1.300
0.600
1.500
2.250
1.350
1.900
1.450
0.8SO
1.600
0.600
0.550
0.800
0.575
1.900
00610
NH3-N
TOTAL
MG/L
0.050
0.140
0.015
0.040
0.464
0.104
0.050
C.I 35
0.100
0.120
0.020
0.020
0.095
0.040
0.090
00671
PHOS-DIS
ORTHO
MG/L P
0.035
0.130
0.040
0.025
0.232
0.144
0. 100
0.070
0.060
0.180
0.125
0.045
0.015
0.030
0.180
00665
PHOS-TOT
MG/L P
0.102
0.160
0.050
0.040
C.315
0.190
0.240
0.150
0.190
0.310
0.190
0.110
0.090
0.070
0.290
-------
STORET RETRIEVAL DATE 76/05/04
2014F1
39 39 44.0 096 48 22.0 4
COON CREEK
20 7.5 BARNES
T/TUTTLE CREEK RESERVOIR 091191
SEC kD BROG 3.5 MI SW OF WATERVlLLE
11EPALES 2111204
0000 FEET DEPTH CLASS 00
DATE
FROM
TO
74/10/13
74/11/10
74/12/15
75/02/09
75/03/09
75/04/13
75/05/18
75/06/14
75/06/29
75/07/13
75/07/27
75/08/10
75/09/14
00630 00625
TIME DEPTH N02S.N03 TOT KJEL
OF N-TOTAL N
DAY FEET
09
11
14
14
14
14
12
12
14
14
14
15
14
55
15
50
40
40
55
10
05
50
30
15
35
50
MG/L
0
0
0
1
1
0
0
1
1
0
0
0
1
.240
.704
.940
.650
.780
.960
.430
.570
.500
.390
.330
.230
.150
MG/L
3.
1.
0.
2.
1.
1.
1.
7.
1.
0.
2.
1.
0.
200
500
500
300
100
800
500
300
050
600
500
700
900
00610 00671 00665
NH3-N PMOS-OIS PHOS-TOT
TOTAL ORTHO
MG/L
0.
0.
0.
0.
0.
0.
0.
1.
0.
0.
0.
0.
0.
055
095
020
432
220
230
025
950
030
015
200
025
020
MG/L
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
P
015
035
005
160
073
100
030
490
125
020
040
020
105
MG/L P
0.135
0.110
0.330
0.110
0.210
0.185
0.750
0.210
0.110
0.130
0.130
0.210
-------
STORET RETRIEVAL DATE 76/05/04
DATE TIME DEPTH
FROM OF
TO GAY FEE:T
74/10/13 09 ?4
74/H/io 10 20
74/12/15 14 00
75/02/09 14 10
75/03/09 13 50
75/04/13 14 ,5
75/05/18 11 30
75/06/14 11 40
75/06/29 14 23
75/07/13 14 00
75/07/27 13 45
75/08/10 16 15
75/09/14 14 30
U0630
N02&N03
N-TOTAL
MG/L
0*T O A
. 780
1.010
1.160
1.500
1.355
0.830
0.015
1.050
1.050
0.010
2.700
0.250
0.0 1 ^
• V A ^J
00625
TOT KJEL
N
MG/L
1.700
1.200
0.4QO
1.675
2.100
1.550
1.500
2.600
2.800
1.750
5.200
3.150
1 .600
00610
NH3-N
TOTAL
MG/L
0.045
0.390
0.082
0.208
0.306
0.080
0.015
0.065
0.025
0.040
0.065
0.015
0.010
00671
PHOS-OIS
ORTHO
MG/L P
0.280
0.250
0.205
0.208
0.288
0.230
0.180
0.270
0.270
0.260
0.260
0.310
0.200
2014G1
39 46 33.0 096 51 29.0 4
LITTLE BLUE RIVER
20 7.5 HANOVER SE
T/TUTTLE CREEK RESERVOIR 091191
KS H»r 15E BROG 5 Ml N OF BARNES
11EPALES 2111204
0000 FEET DEHTM CLASS 00
00665
PHOS-TOT
MG/L P
0.375
0.330
0.260
0.395
0.580
0.320
0.400
1.100
1.050
0.540
1.850
0.580
0.430
-------
STORE! RETRIEVAL DATE 76/05/04
DATE TIME DEPTH
FROM OF
TO DAY FEET
74/10/13 10 38
74/11/10 11 45
74/12/15 15 30
75/01/12 16 00
75/03/09 15 15
75/03/08 15 15
75/04/13 15 25
75/05/18 13 00
75/06/14 12 «o
75/06/29 15 30
75/07/13 15 10
75/07/27 14 40
75/09/14 15 30
00630
N02&N03
N-TOTAL
MG/L
0.072
0.368
0.640
0.880
2.100
1.935
1.250
0.230
1.900
1.300
0.030
0.010
0.095
00625
TOT KJEL
N
MG/L
1.900
1.300
1.400
0.600
2.500
1.450
1.^25
1.250
4.050
0.900
0.950
1.150
1.300
00610
NH3-N
TOTAL
MG/L
0.035
0.470
0.020
0.016
0.232
0.224
0.145
0.025
0.092
0.015
0.030
0.020
0.010
00671
PMOS-DIS
ORTHO
MG/L P
0.085
0.105
0.025
0.035
0.168
0.140
3.115
0.055
0.135
0.120
0.040
0.040
0.082
00665
PHOS-TOT
MG/L P
0.165
0.150
0.110
0.060
0.480
0.200
0.202
0.160
0.280
0.200
0.170
0.150
0.190
3014H1
39 49 53.0 096 38 43.0 4 .
SPRING CREEK
20 7.5 MARYSVILLE
T/TUTTLE CREEK RESERVOIR 091191
US h*Y 77 8RDG .5 MI S OF MARYSVILLE
11EPALES 2111204
0000 FEET DEPTH CLASS 00
-------
STORE? RETRIEVAL DATE 76/C5/04
2014J1
39 42
-------
STORET RETRIEVAL DATE 76/05/04
DATE TIME DEPTc
FROM OF
TO DAY FEET
74/10/13
74/11/10
74/12/15
75/03/09
75/03/09
75/04/13
75/05/18
75/06/14
75/06/29
75/07/12
75/07/29
75/OB/09
75/09/14
13 35
14 15
13 40
14 40
14 30
14 55
09 40
12 19
16 55
14 10
20 20
09 50
15 25
2014K1
39 41 50.0 096 25 07.0 4
BLACK VERMILLION RIVER
20 7.5 FRANKFORT
T/TUTTL-E CREEK RESERVOIR 091191
AT nwr. 99 BROG DUE S OF FRANKFORT
11EPALES 2111204
0000 FEET DEPTH CLASS 00
)0630
JS.N03
rOTAL
1G/L
0.040
1.240
0.600
2.300
1.690
0.760
0.560
1.900
0.950
0.340
0.080
0.050
0.315
00625
TOT KJEL
N
MG/L
2.150
2.600
0.900
2.100
2.000
1.950
1.200
4.200
1.100
1.100
0.850
0.950
1.100
00610
NH3-N
TOTAL
MG/L
0.775
0.110
0.025
0.432
0.304
0.120
0.040
0.075
0.030
0.045
0.020
0.025
0.035
00671
PHOS-DIS
ORTHO
MG/L P
0.115
0.130
0.060
0.128
0.104
0.080
0.085
0.130
0.145
0.080
0.075
0.085
0.090
00665
PHOS-TOT
MG/L P
0.240
0.400
0.100
0.270
0.230
0.170
0.210
0.380
0.300
0.180
0.180
0.170
0.230
-------
STORET RETRIEVAL DATE 76/05>04
DATE TIME OEPT>
PROM OF
TO DAY FEET
74/10/13
74/H/io
74/13/15
75/03/09
75/03/09
75/04/13
75/05/18
75/06/14
75/06/29
75/07/13
75/07/39
75/08/09
75/09/14
13 20
13 40
13 50
13 45
13 45
14 15
09 07
11 51
14 40
14 00
20 10
09 30
15 15
00630
•2&N03
TOTAL
MG/L
0.072
0.960
0.600
2.200
1.585
1.000
0.700
2.000
1.300
0.400
0.550
0.100
0.345
00625
TOT KJEL
N
MG/L
2.500
2.800
1.000
3.300
1.700
2.100
1.550
3.700
1.400
1.100
1.100
2.300
1.900
00610
NH3-N
TOTAL
MG/L
0.420
0.150
0.040
0.360
0.336
0.075
0.060
0.240
0.025
0.035
0.065
0.090
00671
PHOS-OIS
ORTMO
MG/L P
0.185
0.135
0.090
0.160
0.140
3.115
0.115
0.145
0.160
0.095
0.095
0.140
0.140
00665
PHOS-TOT
MG/L P
0.430
0.440
0.140
0.310
0.330
0.330
0.300
0.460
0.370
0.390
0.370
0.340
0.310
3014*2
39 <»0 55.0 096 26 30.0 4
BLACK VERMILLION RIVER
20 7.5 FRANKFORT
T/TUTTLE CkEEK RESERVOIR 091191
AT COUNTr ROAD BRIDGE
11EPALES 3111204
0000 FEET DEPTH CLASS 00
-------
STORET RETRIEVAL DATE 76/05/04
DATE TIME DEPTH
PROM OF
TO DAY FEET
74/10/13
74/11/10
74/13/15
75/02/09
75/03/09
75/04/13
75/05/18
75/06/14
75/06/29
75/07/12
75/07/29
75/08/09
75/09/14
14 15
14 00
14 05
14 15
14 05
14 35
09 ?2
12 05
15 10
14 26
20 40
10 10
15 40
2014L1
39 36 35.0 096 26 10.0 4
CLEAR FORK
20 7.5 FRANKFORT SW
T/TUTTLE CREEK RESERVOIR 091191
SEC RO 8ROG 6.5 MI S OF FRANKFORT
11EPALES 2111204
0000 FEET DEPTH CLASS 00
0630
'&N03
OTAL
IG/L
0.040
0.672
0.336
1.400
0.955
0.470
0.430
0.920
0.770
0.570
0.300
0.220
0.850
00625
TOT KJEL
N
MG/L
1.700
1.200
1.000
1.800
1.500
1.200
1.350
4.400
0.650
0.700
0.700
0.750
1.000
00610
NH3-N
TOTAL
MG/L
0.600
0.125
0.015
0.100
0.136
0.055
0.025
0.075
0.015
0.040
0.020
0.045
0.020
00671
PHOS-DIS
ORTHO
MG/L P
0.025
0.085
0.010
0.096
0.048
0.035
0.030
0.055
0.030
0.005
0.010
0.025
0.090
00665
PHOS-TOT
MG/L P
o.loo
0.150
0.030
0.210
0.080
0.120
0.130
0.120
0.060
0.100
0.080
0.100
0.190
-------
STORET RETRIEVAL DATE 76/05/04
2014M1
39 16 29.0 096 33 31.0 4
CEDAR CREEK
20 7.5 TUTTLE CK DM
T/TUTTLE CREEK RESERVOIR 091191
KS nwf 13 1.5 MI NE OF TUTTLE CREEK DAM
IIE^ALES 2111204
0000 FEET DEPTH CLASS 00
00630
DATE TIME DEPTH N02*.N03
FROM OF N-TOTAL
TO DAY FEET MG/L
75/07/17 13 00
00625
TOT KJEL
N
MG/L
00610
NH3-N
TOTAL
MG/L
00671
PHOS-DIS
ORTHO
MG/L P
00665
PHOS-TOT
MG/L P
0.020
0.005K
K VALUE KNOWN TO 8E
LESS THAN INDICATED
-------
STORE! RETRIEVAL DATE 76/05/04
DATE TIME DEPTH N02S.N03
FROM OF
TO DAY FEET
10 55
10 30
10 15
10 20
09 30
10 30
10 35
11 20
10 27
10 32
13 20
10 ?6
15 50
10 00
74/11/09
74/12/14
75/02/08
75/03/08
75/04/05
75/05/05
75/05/24
75/06/14
75/06/29
75/07/17
75/07/22
75/08/10
75/09/13
2014N1
39 31 25.0 096 34 35.0 4
MCINTIRE CREEK
20 7.5 TUTTLE CR DM
T/TUTTLE CREEK RESERVOIR 091191
SEC RD 8RUG 3.5 Ml rt OF JCT KS H*Y
11EPALES 2111204
0000 FEET DEPTH CLASS 00
13
0630
5.N03
OTAL
G/L
1.200
1.400
1.640
2.700
1.335
0.840
0.850
1.050
1.880
1.880
2.000
2.000
1.900
2.400
00625
TOT KJEL
N
MG/L
2.400
1.100
0.300
0.500
1.400
0.850
0.850
0.500
0.900
0.250
0.250
1.600
0.750
0.950
00610
NH3-N
TOTAL
MG/L
0.040
0.045
0.015
0.030
0.028
0.075
0.045
0.035
0.060
0.015
0.025
0.030
0.090
0.030
00671
PHOS-DIS
ORTHO
MG/L P
0.015
0.135
0.035
0.096
0.032
0.045
0.030
0.050
0.070
0.055
0.065
0.055
0.035
0.055
00665
PHOS-TOT
MG/L P
0.050
0.160
0.040
0.096
0.032
0.090
0.040
0.075
0.080
0.070
0.080
0.065
0.100
0.070
-------
STORET RETRIEVAL DATE 76/05/04
DATE TIME DEPTH N02&N03
FROM OF
TO DAY FEET
74/10/13
74/11/10
75/02/09
75/03/09
75/04/13
75/05/18
75/06/29
75/07/12
75/07/29
75/08/09
75/09/13
12 55
13 30
13 15
13 50
13 30
14 00
08 31
14 25
14 50
19 30
09 14
15 00
2014P1
39 35 55.0 096 32 20.0 4
CORNDODGER CREEK
20 7.5 BLUE RAPIDS
T/TUTTLE CREEK RESERVOIR 091191
SEC RO BROG 1.2 Ml S OF JCT KS H*Y 9
11EPALES 2111204
0000 FEET DEPTH CLASS 00
0630
&N03
OTAL
G/L
0.032
0.810
0.528
2.200
1.585
0.310
0.400
1.100
0.770
0.165
0.095
0.450
00625
TOT KJEL
N
MG/L
2.400
1.200
1.000
1.600
0.800
1.300
O.fiSO
0.600
0.750
0.650
2.200
0.800
00610
NH3-N
TOTAL
MG/L
0.075
0.060
0.030
0.110
0.112
0.020
0.080
0.045
0.020
0.050
0.035
00671
PHOS-DIS
ORTHO
MG/L P
0.015
0.022
0.005
0.056
0.016
0.007
0.005*
0.025
0.005K
0.005K
0.015
0.035
00665
PHOS-TOT
MG/L P
0.110
0.110
0.020
0.120
O.OSO
0.040
0.070
0.060
0.040
0.040
0.060
0.090
K VALUE KNOWN TO BE
LESS THAN INDICATED
-------
STORET RETRIEVAL DATE 76/05/04
DATE TIME DEPTH
FROM OF
TO DAY FEET
75/02/10 11 00
CP(T)-
75/02/10 16 00
75/03/05 11 00
CPU>-
75/03/05 16 00
75/0"»/07 11 00
CP-
75/0<»/28 16 00
75/05/12 11 00
CP-
75/05/12 16 00
75/06/02 11 00
CP < T ) -
75/06/02 16 00
75/06/23 11 00
CP < T ) -
75/06/23 16 00
75/07/14 11 00
CP < T ) -
75/07/14 16 00
75/08/12 11 00
CP-
75/08/12 16 00
75/08/27 11 00
CP < T ) -
75/08/27 16 00
75/09/15 11 00
CP(T>-
75/09/15 16 00
75/10/01 10 00
CP(T>-
75/10/01 17 00
00630
N02&N03
N-TOTAL
MG/L
1.840
4.000
2.480
3.300
1.600
5.400
5.100
2.400
0.025
0.150
0.025
0.100
00625
TOT KJEL
N
MG/L
30.000
31.000
26.000
28.000
30.000
22.000
35.000
16.500
23.500
15.000
27.000
25.000
2014AA PR2014AA P003740
39 50 00.0 096 38 00.0 4
MARYSVILLE
20 7.5 MAPYSVILLE
T/TUTTLE CHEEK 091191
BLUE RIVER
11EPALES 2101204
0000 FEET DEPTH CLASS 00
00610 00671 00665 50051 50053
NH3-N PHOS-DIS PHOS-TOT FLOW CONDUIT
TOTAL ORTHO RATE FLOrf-MGO
MG/L MG/L P MG/L P INST MOD MONTHLY
6.420 3.900 7.800 0.346
7.000
5.200
9.000
3.100 10.000
12.000 0.346
4.000 10.500 0.340
4.300 1.930 4.100 0.346
0.346
0.346 0.346
0.346
3.450 6.100 0.346 0.346
0.346
0.346
10.500 1.880 8.900 0.351 0.346
4.000 0.875 4.500 0.346 0.346
8.300 4.300 9.000 0.346 0.346
3.500 3.050 4.100 0.346 0.346
11.500 3.600 12.500 0.346 0.346
7.100 4.300 10.500 0.346 0.346
-------
STORET RETRIEVAL DATE 76/05/04
00630
DATE TIME DEPTH N02&N03
FROM OF N-TOTAL
TO DAY FEET MG/L
75/10/33 11 00
CP < T) -
75/10/33 16 00
0.050
30.000
2014AA PR2014AA P003740
39 50 00.0 096 38 00.0 4
MARYSVILLE
20 7.5 MARYSVILLE
T/TUTTLE CREEK 091191
BLUE WIVEK
11EPALES 2141204
0000 FEET DEPTH CLASS 00
00625
TOT KJEL
N
MG/L
00610
NH3-N
TOTAL
MG/L
00671
PHOS-DIS
ORTHO
MG/L P
0066S
PHOS-TOT
MG/L P
50051
FLO*
RATE
INST MOD
50053
CONDUIT
FLOW-MGO
MONTHLY
9.200
3.600
6.100
0.346
0.346
-------
STORE! RETRIEVAL DATE 76/05/04
DATE TIME DEPTH N02&N03
FROM OF
TO DAY FEET
75/03/03
75/04/29
75/05/13
75/06/02
75/06/19
75/06/30
75/07/17
75/08/25
75/09/22
75/10/24
75/12/03
75/12/22
13 45
07 45
15 20
08 00
10
11
30
15
09 30
14 10
09 05
08 25
10
11
10
35
2014AB PR2014AB P001298
39 41 30.0 096 39 00.0 4
BLUE RAPIDS
20 7.5 BLUE RAPIDS
T/TUTTLE CREEK 091191
BLUE RIVEH
11EPALES 2141204
0000 FEET DEPTH CLASS 00
0630
1&N03
OTAL
IG/L
0.240
0.100
0.050
0.050
0.150
0.150
0.025
0.100
0.050
0.050
0.025
0.050
00625
TOT KJEL
N
MG/L
43.000
40.000
45.000
30.000
26.000
34.000
31.000
30.000
38.500
44.000
48.000
47.000
00610
NH3-N
TOTAL
MG/L
24.000
28.000
23.000
23.000
15.000
20.000
20.000
22.000
25.000
26.000
30.000
30.000
00671
PHOS-OIS
ORTHO
MG/L P
2.800
2.300
4.600
3.270
1.850
0.650
3.000
9.200
3.200
4.700
4.100
3.300
00665
PHOS-TOT
MG/L P
14.500
16.000
8.100
4.900
8.500
9.400
9.100
10.000
11.500
12.000
13.500
11.500
50051
FLOW
RATE
INST MGD
0.166
0.168
0.167
0.162
0.176
0.192
0.158
0.169
0.158
0.184
0.177
0.183
50053
CONDUIT
FLOW-MOD
MONTHLY
0.162
0.175
0.170
0.161
0.187
0.181
0.162
0.171
0.165
0.174
0.175
0.175
-------
5TOPET RETRIEVAL DATE 76/05/04
2014GA PR2014GA P000750
39 42 00.0 096 44 30.0 4
KATtRVILLE
20 7.5 BAHNES
T/TUTTLE CREEK 091191
LITTLE BLUE RIVER
11EPALES 2141204
0000 FEET DEPTH CLASS 00
DATE
FROM
TO
75/02/12
75/03/11
75/04/16
75/04/30
75/05/22
75/06/12
75/07/02
75/07/24
75/08/13
75/09/03
75/09/23
75/10/14
75/11/05
00630
TIME DEPTH N02&N03
OF N-TOTAL
DAY FEET
09
09
10
10
08
15
09
13
10
15
15
16
oa
10
25
00
30
30
00
00
30
35
50
30
00
45
MG/L
1.760
2.640
1.750
0.700
1.100
0.050
0.125
0.100
0.100
0.025
0.025
0.075
0.150
00625
TOT KJEL
N
MG/L
23
45
45
46
48
42
39
31
39
40
44
36
42
.000
.000
.000
.000
.000
.500
.000
.000
.000
.000
.000
.000
.000
00610 00671
NH3-N PHOS-DIS
TOTAL ORTMO
MG/L
21.
17.
18.
24.
22.
17.
2?.
20.
21.
30.
18.
19.
21.
000
000
800
000
000
300
000
000
000
000
500
500
000
MG/L P
5.500
3.300
2.950
3.100
2.100
6.800
1.100
2.200
1.400
3.300
2.900
2.100
2.500
00665
PHOS-TOT
50051 50053
FLOW CONDUIT
RATE FLO*-MGO
MG/L P INST MGO MONTHLY
6.000
7.300
8.200
13.500
8.000
13.000
6.800
6.500
6.500
9.900
11.500
12.000
7.600
0.067
0.060
0.075
0.083
0.060
0.068
0.067
0.067
0.052
0.075
0.060
0.071
0.067
0.060
0.066
0.067
0.004
0.067
0.090
0.075
0.090
0.090
0.067
0.075
0.067
-------
STORE! RETRIEVAL DATE 76/05/04
2014G6 P82G14GB P000838
39 53 05.0 096 53 00.0 4
HANOVER
20 7.5 HANOVER WEST
T/TUTTLE CHEEK 091191
LITTLE BLUE RIVER
11EPALES 2141204
0000 FEET DEPTH CLASS 00
DATE
FROM
TO
75/02/26
75/04/03
75/04/30
75/06/11
75/07/08
75/07/23
75/08/20
75/09/03
75/09/19
75/10/15
75/10/24
75/12/09
75/12/22
TIME DEPTH
OF
DAY FEET
13 30
15 00
14 30
09 30
11 30
15 00
14 00
15 30
09 00
14 00
15 00
14 00
13 30
00630
N02&N03
N-TOTAL
MG/L
1.520
0.664
1.450
1.000
0.150
0.075
0.100
0.150
0.075
0.075
0.200
0.100
0.150
00625
TOT KJEL
N
MG/L
61.000
51.000
52.500
33.000
53.000
35.000
44.000
50.000
58.000
66.000
50.000
74.500
63.000
00610
NH3-N
TOTAL
MG/L
24.000
27.600
22.000
14.000
32.000
21.000
23.000
35.000
38.000
36.000
31.000
36.000
34.000
00671
PHOS-DIS
ORTHO
MG/L P
8.900
9.200
7.900
4.900
8.000
8.800
9.000
8.200
12.000
12.600
12.000
7.800
10.000
00665
PHOS-TOT
MG/L P
18.500
18.500
22.000
7.050
8.800
10.500
23.000
17.500
15.500
21.000
23.500
22.500
26.000
50051 50053
FLOW CONDUIT
RATE FLOK-MGD
INST MGD MONTHLY
0.001
0.067
-------
STORE! RETRIEVAL DATE 76/05/04
DATE TIME DEPTH N02&N03
FROM OF
TO DAY FEET
75/01/22
75/02/28
75/03/18
75/06/25
75/07/09
75/07/30
75/09/0*
75/09/17
75/10/08
75/11/12
75/12/11
76/01/15
76/02/17
10 00
11 45
08 30
09 00
09 00
13 00
13 00
09 00
15 00
14 30
09 00
2014KA P02014KA P000296
39 51 35.0 096 25 40.0 4
BEATTIE
20 7.5 AXTELL Nw
T/TUTTLE CREEK RES 091191
XOLF CREEK
11EPALES 2141204
0000 FEET DEPTH CLASS 00
0630
S.N03
OTAL
G/L
0.080
2.000
1.440
1.300
0.075
0.025
0.025
0.150
0.075
0.500
1.500
0.850
00625
TOT KJEL
N
MG/L
29.000
52.000
18.000
45.000
27.000
20.000
11.500
10.300
6.200
8.500
12.000
39.000
16.000
00610
NH3-N
TOTAL
MG/L
25.000
11.600
24.000
12.000
0.120
0.089
0.280
0.160
0.075
0.055
12.600
00671
PHOS-DIS
ORTHO
MG/L P
3.900
5.750
4.100
1.400
2.400
3.700
2.800
4.500
3.050
2.880
3.500
2.800
00665
PHOS-TOT
MG/L P
10.000
7.200
29.000
7.600
5.300
4.700
4.200
5.250
3.SOO
3.600
4.700
11.000
50051
FLOW
RATE
INST MGD
0.025
0.028
0.028
0.028
0.028
0.028
0.028
0.028
0.028
0.028
0.028
0.028
0.028
50053
CONDUIT
FLOW-MGD
MONTHLY
0.023
0.028
0.028
0.028
0.028
0.028
0.028
0.028
0.028
0.028
0.028
0.028
0.028
-------
STORET RETRIEVAL DATE 76/05/04
2014KB PD2014KB P001060
39 42 00.0 096 26 00.0 4
FRANKFORT
20 7.5 FRANKFORT
T/TUTTLE CREEK 091191
bLACK VERMILLION RIVER
11EPALES 2141204
0000 FEET DEPTH CLASS 00
DATE
FROM
TO
75/02/14
75/03/14
75/04/15
75/05/09
75/05/27
75/06/16
75/07/08
75/07/29
75/08/13
75/09/04
75/09/24
75/10/15
75/11/10
00630 00625
TIME DEPTH N02&N03 TOT KJEL
OF N-TOTAL N
DAY FEET
15
11
16
09
14
14
09
10
11
09
08
08
09
00
45
00
00
30
00
30
00
30
00
00
00
00
MG/L
0.080
0.160
0.560
0.650
1.150
0.050
0.100
0.100
0.275
0.175
0.875
1.100
1.250
MG/L
2.600
17.000
4.200
11.500
9.200
4.300
12.500
14.000
13.500
18.000
31.000
16.000
12.500
00610 00671 00665
NH3-N PHOS-OIS PHOS-TOT
TOTAL ORTHO
MG/L
0
0
0
0
0
0
0
0
0
0
0
0
0
.271
.160
.080K
.160
.061
.050K
.025
.025K
.110
.025K
.025
.025K
.025
MG/L
5.
4.
0.
1.
2.
0.
2.
1.
3.
2.
3.
3.
4.
P
100
300
180
300
900
860
700
900
600
750
500
850
800
50051 50053
FLOW CONDUIT
RATE FLOW-MOD
MG/L P INST MOD MONTHLY
5.700
1.600
2.500
3.400
1.100
4.100
3.000
4.400
4.100
5.800
5.300
6.100
0.108
0.132
0.120
0.120
0.018
0.180
0.144
0.108
0.120
0.144
0.084
0.096
0.096
0.116
0.143
0.325
0.220
0.200
0.300
0.207
0.104
0.160
0.327
0.155
0.205
0.130
K VALUE KNOWN TO BE
LESS THAN INDICATED
-------
STORET RETRIEVAL DATE 76/05/04
2014WA TF2014WA P001700
39 49 30.0 097 02 30.0 4
WASHINGTON
20 7.5 WASHINGTON
T/TUTTLE CREEK 091191
PEACH CSEEK
11EPALES 3141204
0000 FEET DEPTH CLASS 00
DATE
FROM
TO
75/02/20
75/03/20
75/04/22
75/05/06
75/06/05
75/10/01
75/10/16
75/11/12
75/11/19
75/12/03
75/12/09
75/12/23
00630
TIME DEPTH N02&N03
OF N-TOTAL
DAY FEET
11
11
10
09
09
10
11
10
09
09
13
00
00
30
00
00
30
00
30
30
00
30
MG/L
13.
18.
25.
40.
27.
18.
19.
21.
27.
22.
17.
16.
800
400
000
000
000
900
000
000
000
000
600
000
00625
TOT KJEL
N
MG/L
20.
2.
7.
10.
5.
?.
11.
8.
5.
7.
14.
15.
000
600
450
500
550
800
000
700
000
600
000
000
00610 00671
NH3-N PHOS-DIS
TOTAL ORTHO
MG/L
5.
1.
0.
0.
0.
0.
0.
0.
0.
0.
1.
3.
940
500
530
640
750
056
240
075
510
440
650
600
MG/L
10.
12.
13.
17.
9.
9.
10.
10.
12.
11.
10.
P
000
000
000
300
000
000
500
000
600
000
000
00665 50051 50053
PHOS-TOT FLOW CONDUIT
RATE FLOw-MGD
MG/L P INST MOD MONTHLY
10.500
12.500
1<».000
9.400
9.400
12.000
12.000
13.500
13.000
13.000 0.002
12.500
-------
STORET RETRIEVAL DATE 76/05/04
2014XA TF2014XA P00051'
39 52 00.0 096 15 00.0 4
AXTELL
20 7.5 AXTELL
T/TUTTLE CREEK 091191
VERMILLION
11EPALES 2141204
0000 FEET DEPTH CLASS 00
DATE
FROM
TO
75/04/14
75/05/14
75/06/13
75/07/09
75/09/17
75/10/15
75/11/19
75/12/03
76/01/20
TIME DEPTH
OF
DAY FEET
13 00
08 30
08 30
09 15
09 00
10 30
11 05
10 30
IS 10
00630
N02&N03
N-TOTAL
MG/L
3.750
28.000
4.200
22.000
22.000
28.000
0.150
0.350
2.630
00625
TOT KJEL
N
MG/L
28.000
5.800
19.000
9.200
17.500
15.000
50.000
45.000
43.000
00610
NH3-N
TOTAL
MG/L
11.000
0.050K
5.500
0.025K
2.100
0.830
28.000
21.000
00671
PHOS-DIS
ORTHO
MG/L P
6.000
3.750
3.700
7.500
11.000
9.500
3.500
2.200
3.450
00665
PHOS-TOT
MG/L P
11.000
9.900
6.100
12.000
12.000
12.500
11.000
10.500
14.000
50051
FLOW
RATE
INST MOD
50053
CONDUIT
FLOW-MOD
MONTHLY
K VALUE KNOWN TO BE
LESS THAN INDICATED
-------
STORE! RETRIEVAL DATE 76/05/04
2C14YA AS2014YA i'000145
39 26 00.0 096 45 00.0 4
RANDOLPH
20 7.5 RANDOLPH
T/TUTTLE CREEK 0911*1
PEACH CREEK
11EPALES 2141204
0000 FEET DEPTH CLASS 00
00630 006?5
DATE TIME DEPTH N02&N03 TOT KJEL
FROM OF N-TOTAL N
TO DAY FEET MG/L MG/L
75/04/15 11 00
CP(T)- 0.400 8.800
75/04/15 16 00
75/05/20 08 00
CP(T>- 0.050 13.500
75/05/20 16 00
75/06/18 08 00
CP ( T ) -
75/06/18 17 00
75/07/20 08 00
CP(T)-
75/07/20 17 00
75/08/19 08 00
CP-
75/08/19 16 00
75/09/17 08 30
CP(T)-
75/09/17 19 30
75/10/26 08 30
cpm-
75/10/26 15 00
75/11/23 09 00
CPITI-
75/11/23 15 00
75/12/24 08 00
76/01/18 08 00
CP-
76/01/18 15 00
76/02/13 08 00
CP(T>-
76/02/13 15 00
76/03/21 08 00
CP < T ) -
76/03/21 17 00
'••000 5.400
0.025 3.200
0.050 26.000
0.025 23.500
3.000 31.000
9.200 11.000
3.500 24.000
17.000
19.000
23.000
00610 00671 0066S
NH3-N PHOS-OIS PHOS-TOT
TOTAL ORTHO
MG/L MG/L P MG/L P
5.000
0.570 1.550 8.000
0.050K 3.800 5.200
0.030 2.400 7.700
8.200 1.200 8.000
7.300 1.150 7.200
6.000 2.200 10.500
0.380 5.400 7.800
5.600 4.700 7.000
1.800 7.650
8.600
9.800
50051
FLO*
RATE
INST MGO
0.012
0.013
0.012
0.001
0.009
0.005
0.005
0.010
50053
CONDUIT
FLO*-MGD
MONTHLY
0.010
0.015
0.013
0.010
0.006
0.005
0.009
K VALUE KNOHN TO BE
LESS THAN INDICATED
-------
STORET RETRIEVAL DATE 76/05/04
2014ZA TF2014ZA P000485
39 43 00.0 096 59 00.0 4
GREENLEAF
20 7.5 GREENLEAF
T/TUTTLE CREEK 091191
UNNAMED STREAM
11EPALES 2141204
0000 FEET DEPTH CLASS 00
DATE
FROM
TO
75/02/24
75/04/07
75/05/19
75/06/10
75/06/25
75/08/05
75/09/16
75/10/08
75/10/24
75/11/06
75/12/05
75/12/09
00630
TIME DEPTH N02&N03
OF N-TOTAL
DAY FEET
15
14
13
13
13
10
13
13
13
13
13
13
00
00
00
30
45
00
00
30
00
30
30
30
MG/L
7.
11.
11.
• 4.
10.
0.
20.
23.
3.
27.
14.
24.
360
050
000
300
000
675
000
000
400
000
700
000
00625
TOT KJEL
N
MG/L
22.000
26.000
31.000
27.500
24.000
24.000
4.700
9.700
37.000
25.000
23.000
16.000
00610 00671 00665 50051 50053
NH3-N PHOS-DIS PHOS-TOT FLOW CONDUIT
TOTAL ORTHO RATE FLO*-MGD
MG/L
5
4
9
10
1
6
18
7
3
.125
.400
.100
.000
.200
.200
.000
.050
.000
MG/L
3.
2.
5.
4.
2.
4.
7.
8.
8.
7.
8.
10.
P
700
240
600
000
600
900
500
400
500
800
950
000
MG/L
9.
10.
12.
10.
11.
7.
8.
8.
12.
5.
13.
11.
P INST MGO MONTHLY
000
500
500
500
500
900
000
700
500
300
000
500
------- |