U.S. ENVIRONMENTAL PROTECTION AGENCY
NATIONAL EUTROPHICATION SURVEY
WORKING PAPER SERIES
REPORT
ON
MILFORD RESERVOIR
CLAY AND GEARY COUNTIES
KANSAS
EPA REGION VII
WORKING PAPER No, 519
CORVALLIS ENVIRONMENTAL RESEARCH LABORATORY - CORVALLIS, OREGON
and
ENVIRONMENTAL MONITORING & SUPPORT LABORATORY - LAS VEGAS, NEVADA
699-440
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REPORT
ON
MILFORD RESERVOIR
CLAY AND GEARY COUNTIES
KANSAS
EPA REGION VII
WORKING PAPER No, 519
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 3
III. Lake Water Quality Summary 4
IV. Nutrient Loadings 9
V. Literature Reviewed 14
VI. Appendices 15
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11
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)J, clean lakes [§314(a,b)],
and water quality monitoring [§106 and §305(b)] activities mandated
by the Federal Water Pollution Control Act Amendments of 1972.
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TM
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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•LJ
Map Location
MILFORD RESERVOIR
8 Tributary Sampling Site
X Lake Sampling Site
9 Sewage Treatment Facility
Scale
»r30'
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MILFORD RESERVOIR
STORE! NO. 2009
I. CONCLUSIONS
A. Trophic Condition:
Survey data indicate that Milford Reservoir is eutrophic.
It ranked thirteenth in overall trophic quality when the 15
Kansas reservoirs sampled in 1974 were compared using a com-
bination of six lake parameters*. Eleven of the reservoirs
had less median total phosphorus, 11 had less and one had the
same median dissolved phosphorus, nine had less median in-
organic nitrogen, 12 had less mean chlorophyll a_, and three
had greater mean Secchi disc transparency. Depression of
dissolved oxygen with depth occurred at stations 1 and 3 in
June.
Survey limnologists did not observe macrophytes or surface
concentrations of algae but noted turbid water in June and
October at sampling station 4.
B. Rate-Limiting Nutrient:
The algal assay results indicate that Milford Reservoir was
phosphorus limited at the time the assay sample was collected
(04/11/74).
The reservoir data indicate phosphorus limitation at all
sampling times.
See Appendix A.
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C. Nutrient Controllability:
1. Point sources—Point sources contributed 3.2% of the
total phosphorus input to Milford Reservoir during the sampling
year. The City of Clyde added 0.3% of the total; Concordia,
1.2%; Morganville, <0.1%; Wakefield, 0.2%; Clay Center, 1.3%;
and Clifton, 0.2%.
The present phosphorus loading of 6.79 g/m 2/yr is nearly
eleven times that proposed by Vollenweider (Vollenweider and
Dillon, 1974) as a eutrophic loading (see page 13). Because
of the relatively small contributions, it is not likely that
point-source phosphorus control would result in any significant
improvement in the trophic condition of Milford Reservoir.
2. Non-point sources—The contribution of non-point sources
amounted to 96.8% of the total phosphorus load to Milford Reser-
voir during the sampling year. The Republican River contributed
90.8% of the total; Five Creeks, 1.3%; Mall Creek, 0.5%; and the
ungaged tributaries added an estimated 3.9%.
The phosphorus export rates of the Republican River, Five
Creeks, and Mall Creek were 6, 30, and 26 kg/km 2/yr, respectively
(see page 12). These rates compare well to those of three tribu-
taries of nearby Council Grove Reservoir* (60, 41, and 6 kg/km2/
yr, respectively).
* Working Paper No. 512.
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II. RESERVOIR AND DRAINAGE BASIN CHARACTERISTICS"1"
A. Morphometry :
1. Surface area: 65.51 kilometers2.
2. Mean depth: 7.8 meters.
3. Maximum depth: 21.3 meters.
4. Volume: 511.902 x 106 m3.
5. Fourteen-year median hydraulic retention time: 285 days.
B. Tributary and Outlet:
(See Appendix C for flow data)
1. Tributaries -
Drainage Mean flow
Name area (km2)* (m3/sec)*
Republican River 63,563.8 23.530
Five Creeks 179.7 0.570
Mall Creek 54.0 0.263
Minor tributaries &
immediate drainage - 604.5 2.830
Totals 64,402.0 27.193
2. Outlet -
Republican River 64,465.1** 26.170
C. Precipitation***:
1. Year of sampling: 66.6 centimeters.
2. Mean annual: 87.7 centimeters.
t Table of metric conversions—Appendix B.
tt Kring, 1977.
* For limits of accuracy, see Working Paper No. 175, "...Survey Methods,
1973-1976".
** Includes area of reservoir.
*** See Working Paper No. 175.
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III. WATER QUALITY SUMMARY
Mil ford 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 four stations on the reservoir (see map,
page v). During each visit, a single depth-integrated (4.6 m or
near bottom to surface) sample was composited from the stations for
phytoplankton identification and enumeration; and during the first
visit, a single 18.9-liter depth-integrated sample was composited
for algal assays. Also each time, a depth-integrated sample was
collected from each of the stations for chlorophyll a_ analysis.
The maximum depths sampled were 18.0 meters at station 1, 14.0
meters at station 2, 10.1 meters at station 3, and 4.6 meters at
station 4.
The sampling results are presented in full in Appendix D and
are summarized in the following table.
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PARAMETER
TEMP (C)
DISS OXY (MG/L)
CNDCTV/Y (MCROMO)
PH (STAND UNITS)
TOT ALK (MG/L)
TOT P (MG/L)
ORTHO P (MG/L)
N02»N03 (MG/L)
AMMONIA (MG/L)
KJEL N (MG/L)
INORG N (MG/L)
TOTAL N (MG/L)
CHLRPYL A (UG/D
SECCHI (METERS)
A. SUMMARY OF PHYSICAL AND
1ST SAMPLING ( 4/11/74)
<» SITES
CHEMICAL CHARACTERISTICS FOR MILFORO HESERVOI*
STORtT CODE 2009
2ND SAMPLING ( 6/26/74)
4 SITES
RANGE
9.0 - 12.5
9.4 - 10.8
51S. - 681.
8.3 - 8.4
190. - 268.
0.112 - 0.271
0.053 - 0.065
0.450 - 1.200
0.040 - 0.150
0.400 - 1.10C
0.500 - 1.270
1.050 - 1.810
24.4 - 30.7
0.4 - 0.8
3RO SAMPLING (10/ 3/74)
4 SITES
MEAN
10.1
10.2
562.
8.4
211.
0.150
0.059
0.879
0.089
0.662
0.968
1.542
26.3
0.6
MEDIAN
9.5
10.3
535.
8.4
204.
0.12*
0.059
1.000
0.080
0.600
1.060
1.600
25.1
0.6
SANGE
20.8
2.2
742.
8.0
192.
0.043
0.013
0.500
0.070
0.500
0.570
1.030
1.1
0.4
- 24.9
8.2
- 861.
8.4
- 228.
- 0.177
- 0.079
- 0.740
- 0.200
- 0.900
- 0.880
- 1.510
- 16.1
2.7
MEAN
23.2
5.6
772.
8.2
199.
0.085
0.040
0.612
0.143
0.637
0.754
1.248
7.3
1.5
MEDIAN
23.1
5.8
753.
8.2
196.
0.066
0.037
0.590
0.140
0.600
0.760
1.280
6.1
1.4
rJANGE
13.4
7.6
630.
8.3
179.
0.017
0.002
0.020
0.020
0.400
0.040
0.530
8.1
0.3
- 17.0
9.0
- 671.
8.6
- 256.
- 0.116
- 0.025
- 0.360
- 0.080
- 0.700
- 0.390
- 1.000
- 51.1
O.t>
MEAN
16.1
8.3
643.
8.4
191.
0.0*2
0.005
0.215
0.030
0.535
0.245
0.750
22.9
0.5
MEDIAN
16.7
8.2
637.
8.4
185.
0.026
0.002
0.220
0.020
0.500
0.240
0.720
16.3
0.6
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B. Biological Characteristics:
1. Phytoplankton -
Sampling
Date
04/11/74
06/26/74
10/03/74
Dominant
Genera
1.
2.
3.
4.
5.
1.
2.
3.
4.
5.
1.
2.
3.
4.
5.
Algal Units
peir ml
20,
759
801
450
225
135
180
Stephanodiscus sp.
Chroomonas sp.
Ankistrodesmus sp.
Cryptomonas sp.
Nitzschia sp.
Other genera 180
Total 23,550
Centric diatoms 284
Microcystis sp. 236
Scenedesmus' sp. 189
Cryptomonas sp. 142
Nitzschia sp. 142
Other genera 379
Total 1,372
Stephanodiscus sp. 5,182
Chroomonas sp. 790
Skeletonema sp. 740
Dactylococcopsis sp. 296
Scenedesmus sp. 197
Other genera 395
Total
7,600
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2. Chlorophyll a_ -
Sampling
Date
04/11/74
06/26/74
10/03/74
Station
Number
1
2
3
4
1
2
3
4
1
2
3
4
Chlorophyll a
(yg/1)
24.6
24.4
25.7
30.7
1.1
4.3
7.9
16.1
8.1
16.8
15.8
51.1
C. Limiting Nutrient Study:
1. Autoclaved, filtered, and nutrient spiked -
Ortho P
Cone, (mg/1)
Inorganic N Maximum yield
Cone, (mg/1) (mg/1-dry wt.)
0.025
0.075
0.075
0.025
0.465
0.465
1.465
1.465
12.6
16.3
25.2
13.3
Spike (mg/1)
Control
0.050 P
0.050 P + 1.0 N
1.0 N
2. Discussion -
The control yield of the assay alga, Selenastrum capri-
cornutum, indicates that the potential primary productivity
of Mil ford Reservoir was high at the time the sample was
taken (04/11/74). There was a significant increase in yield
when phosphorus alone was added, but no such increase occurred
when only nitrogen was added. These results indicate the
reservoir was phosphorus limited at that time.
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8
The reservoir data also indicate phosphorus limitation.
The mean inorganic nitrogen to orthophosphorus ratios were
16 to 1 in April, 19 to 1 in June, and 49 to 1 in October;
and phosphorus limitation would be expected.
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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 map (page v), except for the months
months of June and July when two samples were collected at most 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/km2/year, at stations B-l and D-l and multi-
plying the means by the ZZ area in km2.
The operators of the Clifton, Clyde, Concordia, and Morganville
wastewater treatment plants provided monthly effluent samples and
corresponding flow data. The operators of the Clay Center and Wake-
field wastewater treatment plants provided monthly effluent samples
See Working Paper No. 175.
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10
but could not provide flow data. Therefore, nutrient loads from these
two 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
Clay Center
Clifton
Clyde
Concordia
Morganville
Wakefield
Pop.
Served
5,093
714
963
7,680
252
730
Mean Flow
Treatment (m3/d)
prim.
clarifier
Imhoff tank
stab, pond
stab, pond
stab, pond
stab, pond
1,927.7
304.7
529.5
1,063.7
96.9
276.3
Receiving
Water
Republican
River
Republican
River
Republican
River
Republican
River
Buffalo Creek/
Republ ican
River
Mil ford Reser-
voir
2. Known industrial - None
* Treatment plant questionnaires.
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11
B. Annual Total Phosphorus Loading - Average Year:
1. Inputs -
kg P/ % of
Source yr total
a. Tributaries (non-point load) -
Republican River 389,025 90.8
Five Creeks 5,355 1.3
Mall Creek 2,125 0.5
b. Minor tributaries & immediate
drainage (non-point load) - 16,925 3.9
c. Known municipal STP's -
Clay Center 5,775 1.3
Clifton 1,005 0.2
Clyde 1,200 0.3
Concordia 5,145 1.2
Morganville 75 <0.1
Wakefield 830 0.2
d. Septic tanks - Unknown ? ?
e. Known industrial - None
f. Direct precipitation* - 1,105 0.3
Total 428,565 100.0
2. Outputs -
Reservoir outlet - Republican River 48,260
3. Net annual P accumulation - 380,305 kg.
See Working Paper No. 175.
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12
C. Annual Total Nitrogen Loading - Average Year:
1. Inputs -
kg N/ % of
Source yr total
a. Tributaries (non-point load) -
Republican River 1,884,190 79.7
Five Creeks 66,445 2.8
Mall Creek 39,140 1.7
b. Minor tributaries & immediate
drainage (non-point load) - 258,120 10.9
c. Known municipal STP's -
Clay Center 17,320 0.8
Clifton 3,445 0.2
Clyde 2,710 0.1
Concordia 17,365 0.8
Morganville 240 <0.1
Wakefield 2,485 0.1
d. Septic tanks - Unknown ? ?
e. Known industrial - None
f. Direct precipitation* - 68.155 2.9
Total 2,359,615 100.0
2. Outputs -
Reservoir outlet - Republican River 1,327,935
3. Net annual N accumulation - 1,031,680 kg.
D. Non-point Nutrient Export by Subdrainage Area:
Tributary kg P/km2/yr kg N/km2/yr
Republican River 6 30
Five Creeks 30 370
Mall Creek 26 484
See Working Paper No. 175.
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13
E. Mean Nutrient Concentrations in Ungaged Streams:
Mean Total P Mean Total N
Tributary Cone, (mg/1) Cone, (mg/1)
Unnamed Stream C-l 0.219 2.304
Unnamed Stream F-l 1.176
Unnamed Stream G-1 0.050 0.170
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 "dangerous1'
and "permissible".
Note that Vollenweider's model may not be applicable to
water bodies with short hydraulic retention times.
Total Phosphorus Total Nitrogen
Total Accumulated Total Accumulated
grams/m2/yr 6.79 6.02 37.4 16.3
Vollenweider phosphorus loadings
(g/m2/yr) based on mean depth and 14-year median
hydraulic retention time of Milford Reservoir:
"Dangerous" (eutrophic loading) 0.62
"Permissible" (oligotrophic loading) 0.31
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14
V. LITERATURE REVIEWED
Kring, R. Lynn, 1977. Personal communication (revised reservoir
morphometry). KS Dept. of Health & Environment, Topeka.
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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15
VI. APPENDICES
APPENDIX A
LAKE RANKINGS
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LAKE DATA TO BE USED IN RANKINGS
LAKE
CODE LAKE NAME
2001 CEDAR BLUFF RESERVOIR
2003 COUNCIL GROVE
2003 ELK CITY
2004 FALL RIVER RESERVOIR
2005 JOHN REDMOND RESERVOIR
2006 KANOPOLIS RESERVOIR
2007 MARION RESERVOIR
2008 MELVERN RESERVOIR
2009 MILFORn RESERVOIR
2010 NORTON RESERVOIR
2011 PERRY RESERVOIR
2012 POMONA RESERVOIR
2013 TORONTO RESERVOIR
2014 TUTTLE CREEK RESERVOIR
2015 WILSON RESERVOIR
MEDIAN
TOTAL P
0.017
0.069
0.030
0.053
0.118
0.056
0.052
0.034
0.079
0.122
0.055
0.040
0.067
0.162
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
431.333
488.500
470.667
445.222
.MEAN
CHLORA
•-J
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 CRTHO 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.
SANK 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 2003 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 3LUFF RESERVOIR
2003 COUNCIL GROVE
2003 ELK CITY
2004 FALL RIVER RESERVOIR
2005 JOHN REDMOND RESERVOIR
2006 KANOPOLIS RESERVOIR
2007 MARION RESERVOIR
200ft 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 1
86 (
57 (
14 1
43 (
64 -I
79 1
21 (
7 I
50 I
71 l
36 i
0 i
93 l
: 14)
: 4)
: 12)
; a)
I 2)
I 6)
! 9)
[ 11)
I 3).
I 1)
I 7)
! 10)
I 5)
( 0)
( 13)
MEDIAN
INORG N
100 <
29 (
50 <
57 <
0 <
43 <
64 1
82 <
36 (
93 1
18 <
7 1
71 (
18 <
82 (
: 14)
: 4>
: 7)
; 8)
: o)
: 6>
: 9)
: ID
; s>
! 13)
: 2>
: i)
I 10)
[ 2)
[ 11)
500-
MEAN SEC
100 (
36 (
7 (
14 (
0 1
29 <
43 <
36 1
79 <
64 (
57 1
50 <
21 1
71 l
93 1
i 14)
: 5)
; i)
: 2)
; o)
: 4)
: 6)
: 12)
: ID
: 9>
I 8)
! 7)
I 3)
[ 10)
I 13)
MEAN
CHLORA
93 (
43 1
100 (
71 (
50 1
21 (
29 1
0 1
14 1
7 1
86 1
64 1
79 i
36 i
57 1
: 13)
; 6)
: 14)
: 10)
: 7)
; 3)
1 4)
t 0)
I 2)
[ 1)
I 12)
1 9)
t 11)
( 5)
[ 8)
15-
MIN DO
57 1
64 {
7 (
79 1
93 1
71 (
86 1
0 1
50 1
100 1
25 1
39 1
39 i
14 .1
25 l
: a)
: 9)
; i>
: ID
; 13)
: io>
[ 12)
; o
; 7)
[ 14)
[ 3)
[ 5)
! 5)
( 2)
; 3)
MEDIAN
DISS ORTHO P
89 <
29 1
100 <
50 (
7 1
64 (
71 1
79 1
14 1
21 (
43 l
36 1
57 <
0 <
89 1
: 12)
: 4)
; 14)
; 7)
; i)
; 9)
[ 10)
: ID
[ 2)
[ 3)
[ 6)
[ 5)
C 8)
t 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
-4
Cubic meters x 8.107 x 10 = acre/feet
Square kilometers x 0.3861 = square miles
Cubic meters/sec x 35.315 = cubic feet/sec
Centimeters x 0.3937 = inches
Kilograms x 2.205 = pounds
Kilograms/square kilometer x 5.711 = Ibs/square mile
-------
APPENDIX C
TRIBUTARY FLOW DATA
-------
TRIBUTARY FLOw INFORMATION FOR KANSAS
12/0376
CODE 2009
MILFORD
TOTAL DRAINAGE AREA OF LAKE(SO KM)
SUB-ORAINA'3E
TPI6UTAKY ARfAfSQ KM)
NORMALISED FLO*S(CMS>
2009A1
2009A2
2009B1
200901
2009ZZ
64465.1
63563.8
179.7
54.0
614.9
JAN
12.16
10.76
0.24
0.113
1.27
Ftb
20.95
17.56
0.34
0.150
1.67
MAR
24.64
0.74
0.368
3.11
APH-
36.61
23.50
0. 71
0.311
3.68
MAY
45.31
33.96
1.02
0.461
3.11
J'JN
39.64
42.46
1.06
0.453
3.40
JUL . AUG SEP
23.03 17.27 23.22
33. 98 19.62 31.15
1.05 0.34 0.40
0.510 0.150 0.173
b.38 3.11 3.40
OCT
15.57
23.22
0.48
0.216
2.83
NOV
19.54
12.18
0.23
0.099
1.64
13
0
0.
1
•JEC
.03
!24
116
.30
MEAN
26.17
23.53
0.57
0.263
2.H3
SUMMARY
TOTAL
SUM OF
DRAINAGE AREA OF LAKE =
SUB-DRAINAGE AREAS »
64439.2
64412.4
TOTAL FLOW IN =
TOTAL FLOW OUT =
326.
314.
24
03
MEAN MONTHLY FLOWS AND DAILY FLOwS(CMS)
TRIBUTARY MONTH YEAR MEAN FLOW DAY
2009A1
FLO*1 DAY
FLOW DAY
FLOW
2009A2
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
7.419
2.053
1.444
1.317
3.908
16.197
9.231
4.870
58.333
56.917
9.401
2.240
4.389
6.315
6.173
6.116
6.4CO
16.339
11.525
7.051
75.040
23.701
10.449
4.786
12
e
14
11
8
9
24
Ib
20
12
30
29
12
16
8
5
2
1
13
4
8
6
10
6
12.743
2.067
1.331
1.246
1.331
26.674
9.345
2.464
85.517 30
127.426 30
3.455
2.124
3.964
6.?86
6.966
4.672
5.267
25.485
9.514
8.948
30.016 20
38.794 20
9.401
8.155
55.218
8.297
104.772
11.893
-------
TRIBUTARY FLOW INFORMATION FOR KANSAS
12/0376
LA^ONTH YEA*
200901
2009Z2
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
7t
74
74
75
75
75
75
75
75
75
75
75
74
74
74
75
75
75
75
75
75
75
75
75
MEAN FLOW DAY
0.150
0.241
0.263
3.233
0.311
0.425
0.680
0.212
2.520
0.340
0.156
0.096
0.068
0.102
0.125
0.110
0.139
0.212
0.283
0.099
1.048
U.164
0.068
0.042
0.878
.699
.416
.246
.529
.812
3.398
0.651
7.929
1.727
1.416
0.821
1?
16
6
5
2
1
13
4
8
6
10
6
12
16
8
S
2
1
13
4
8
6
10
6
FLOW DAY
rLOw DAY
FLOW
O.OlH
O.OuO
0.054
0.054
0.037
0.198
0.127
0.085
1.133
0.139
0.031
0.042
0.076
0.074
0.071
O.ObS
0.062
0.071
0.035
0.095
0.071
0.057
0.040
0.042
20
20
16
20
7.079
0.065
0.0
0.057
20
0.127
-------
APPENDIX D
PHYSICAL and CHEMICAL DATA
-------
STORET RETRIEVAL DATE 76/05/03
200901
39 04 40.0 096 53 51.0 3
MILFURD RESERVOIR
20.061 KANSA.S
091191
11EPALES 2111202
0042 FEET DEPTH CLASS 00
DATE
FROM
TO
74/04/11
74/06/26
74/10/03
DATE
FROM
TO
74/04/11
74/06/26
74/10/03
TIME DEPTH
OF
DAY FEET
15 00 0000
15 00 0005
15 00 0015
15 00 0037
13 00 0000
13 00 0005
13 00 0022
13 00 0040
13 00 0059
09 05 0000
09 05 0005
09 05 0015
09 05 0030
09 05 0040
TIME DEPTH
OF
DAY FEET
15 00 0000
15 00 0005
15 00 0015
15 00 0037
13 00 0000
13 00 0005
13 00 0022
13 00 0040
13 00 0059
09 05 0000
09 05 0005
09 05 0015
09 05 0030
09 05 0040
00010
WATER
TEMP
CENT
9.1
9.1
9.0
9.0
23.1
23.1
22.5
22.1
20.8
16.9
16.9
16.9
16.9
17.0
00665
PHOS-TOT
MG/L P
C.114
0.113
0.113
0.112
0.075
0.045
0.046
0.083
0.104
0.026
0.026
0.017
0.072
0.026
00300
DO
MG/L
10.
10.
10.
6.
6.
5.
4.
2.
7.
7.
7.
8.
7.
32217
00077 00094
TRANSP CNDUCTVY
SECCHI FIELD
INCHES MICROMHO
30
4
4
2
8 108
6
4
8
2
8 24
8
8
0
6
00031
517
517
516
515
749
750
747
742
743
643
642
645
645
645
00400 00410
PH T ALK
CAC03
SU
8.35
8.4Q
8.40
8.40
8.30
8.30
8.20
8.20
8.10
8.27
8.29
8.31
8.27
8.25
MG/L
212
202
210
204
195
195
198
201
202
185
186
183
186
188
00610 00625 00630 00671
NH3-N TOT KJEL N02&N03 PriOS-DIS
TOTAL N N-TOTAL ORTHO
MG/L
0.080
0.080
0.070
0.100
0.120
0.100
0.130
0.130
0.140
0.020K
0.020K
0.020K
0.020K
0.030
MG/L
0.600
0.400
0.500
0.500
0.600
0.500
0.500
0.600
0.500
0.700
0.500
0.400
0.500
0.500
MG/L
1.140
1.060
1.200
1.110
0.680
0.590
0.640
0.710
0.740
0.300
0.360
0.220
0.360
0.360
MG/L P
0.059
0.062
0.063
0.062
0.070
0.026
0.031
0.039
0.046
0.002
0.004
0.004
0.025
0.015
CHLRPHYL INCDT LT
A O C' U M T fc 1 fl.
UG/L
24.
1.
8.
HEMNING
PERCENT
6
1
1.0
1
K VALUE KNO*N TO BE
LESS THAN INDICATED
-------
STORET RETRIEVAL DATE 76/05/03
300902
39 07 33.0 096 54 57.0 3
MILFORD RESERVOIR
20061 KANSAS
091191
11EPALES 2111202
0050 FEET DEPTH CLASS 00
DATE
FROM
TO
74/04/11
74/06/26
74/10/03
DATE
FROM
TO
74/04/11
74/06/26
74/10/03
TIME DEPTH
OF
DAY FEET
14 35 0000
14 35 0005
14 35 0015
14 35 0030
14 35 0045
13 30 0000
13 30 0005
13 30 0020
13 30 0030
13 30 0041
09 40 0000
09 40 0005
09 40 0015
09 40 0030
09 40 0046
TIME DEPTH
OF
DAY FEET
14 35 0000
14 35 0005
14 35 0015
14 35 0030
14 35 0045
13 30 0000
13 30 0005
13 30 0020
13 30 0030
13 30 0041
09 40 0000
09 40 0005
09 40 0015
09 40 0030
09 40 0046
00010
WATER
TEMP
CENT
9.5
9.4
9.5
9.4
9.4
23.8
23.1
23.0
22.6
22.4
16.8
16.7
lt>.8
16.7
16.7
00665
PHOS-TOT
MG/L P
0.126
0.130
0.119
0.120
0.123
0.045
0.044
0.045
0.043
0.060
0.019
0.024
0.026
0.025
0.036
00300 00077
DO TRANSP
SECCHI
MG/L INCHES
25
10.4
10.6
10.8
10.4
7.6 72
7.0
6.6
6.0
4.6
8.4 24
8.4
8.2
8.2
8.0
32217 00031
CHLRPHYL INCOT LT
A REMNING
UG/L PERCENT
24.4
,
4.3
1.0
16.8
00094
CNDUCTVY
FIELD
MICROMHO
521
521
523
523
547
753
747
744
743
742
637
636
637
637
636
00400
PH
SU
8.
8.
8.
a.
8.
8.
8.
8.
8.
8.
8.
8.
8.
8.
40
40
40
40
40
40
40
30
00
36
35
38
37
34
00410
T ALK
CAC03
MG/L
196
200
192
204
204
193
194
196
192
198
185
185
182
179
180
00610 00625
NH3-N TOT KJEL
TOTAL
MG/L
0.060
0.060
0.060
0.080
0.100
0.070
0.130
0.130
0.130
0.150
0.020K
0.020K
0.020K
0.020K
0.060
N
MG/L
0.800
0.600
0.600
0.600
0.700
0.600
0.500
0.500
0.500
0.600
0.600
0.600
0.600
0.400
0.400
00630
N02&N03
N-TOTAL
MG/L
1.010
1.030
0.990
1.050
1.010
0.500
0.530
0.580
0.540
0.630
0.250
0.310
0.200
0.180
0.300
00671
PHOS-DIS
ORTHO
MG/L P
0.059
0.061
0.060
0.059
0.057
0.013
0.023
0.032
0.025
0.036
0.003
0.002
0.003
0.002
0.002
K VALUE KNOrfN TO 3E
LESS THAN INDICATED
-------
STORET RETRIEVAL DATE 76/05/03
DATE TIME DEPTH
FROM OF
TO DAY FEET
74/04/11 14
14
14
14
74/06/26 14
14
14
14
14
74/10/03 10
10
10
10
15 0000
15 0005
15 0015
15 0030
00 0000
00 0005
00 0015
00 0025
00 0033
15 0000
15 0005
15 0015
15 0025
00010
HATER
TEMP
CENT
10.1
10.0
10.0
10.0
23.5
23.4
23.2
23.0
22.5
16.1
16.1
16.0
16.0
200903
39 11 14.0 096 59 09.0 3
MILFORD RESERVOIR
20061 KANSAS
091191
11EPALES
211
0035 FEET DEPTH CLASS
00300
DO
MG/L
10.2
10.2
10.2
5.8
6.0
5.2
3.8
2.2
8.4
8.4
8.6
8.2
00077
TRANSP
SECCHI
INCHES
20
36
24
00094
CNDUCTVY
FIELD
MICROMHO
565
564
564
565
770
770
765
760
754
630
631
631
631
00400
PH
su
8.35
8.30
8.30
8.30
8.4Q
8.20
8.20
8.10
8.00
8.44
8.41
8.42
8.45
00410
T ALK
CAC03
MG/L
202
198
204
190
196
194
194
194
195
181
181
180
182
00610
NH3-N
TOTAL
MG/L
0.140
0.150
0.140
0.150
0.150
0.140
0.160
0.160
0.200
0.080
0.020
0.020
0.030
1202
00
00625
TOT KJEL
N
MG/L
0.600
0.800
0.800
0.900
0.700
0.600
0.700
0.700
0.700
0.600
0.500
0.500
0.400
00630
N02&N03
N-TOTAL
MG/L
0.730
0.770
0.760
0.750
0.580
0.570
0.580
0.600
0.630
0.220
0.180
0.190
0.130
00671
PHOS-DIS
OftTrtO
MG/L P
0.053
0.054
0.055
0.055
0.037
0.034
0.034
0.037
0.040
0.002K
0.002K
0.002K
0.002K
DATE
FROM
TO
74/04/11
74/06/26
74/10/03
TIME DEPTH
OF
DAY FEET
14 15 0000
14 15 0005
14 15 0015
14 15 0030
14 00 0000
14 00 0005
14 00 0008
14 00 0015
14 00 0025
14 00 0033
10 15 0000
10 15 0005
10 15 0015
10 15 0025
00665 32217 00031
PHOS-TOT CHLRPHYL INCDT LT
A REMNING
MG/L P UG/L PERCENT
0.133 25.7
0.126
0.120
0.158
0.068 7.9
0.066
1.0
0.065
0.068
0.100
0,022 15.8
0.029
0.023
0.030
K VALUE KNOWN TO BE
LESS THAN INDICATED
-------
STORE! RETRIEVAL DATE 76/05/03
DATE TIME DEPTH
FROM OF
TO DAY FEET
74/04/U 13 50
13 50
13 50
74/06/26 14 20
0000
0005
0010
0000
14 20 0005
14 20 0010
14 20 0015
74/10/03 10 45 0000
10 45 0005
10 45 0012
00010
MATER
TEMP
CENT
12.5
12.5
12.4
24.8
24.9
24.1
24.0
13.5
13.5
13.4
200904
39 13 01.0 097 00 15.0 3
MILFOSD RESERVOIR
20027 KANSAS
091191
11EPALES
2111202
0015 FEET DEPTH CLASS
00300
DO
MG/L
9.4
9.8
7.6
8.2
5.6
5.2
9.0
9.0
8.6
00077
TRANSP
SECCHI
INCHES
14
15
12
00094
CNDUCTVY
FIELD
MICHOMHO
681
681
679
838
847
849
861
670
669
671
00400
PH
SU
8.30
8.35
8.30
8.40
8.40
8.20
8.10
8.57
8.53
8.57
00410
T ALK
CAC03
MG/L
268
254
236
199
200
228
226
214
216
256
00610
NH3-N
TOTAL
MG/L
0.040
0.060
0.050
0.130
0.180
0.170
0.190
0.020
0.020
0.070
00
00625
TOT KJEL
N
MG/L
1.100
0.500
0.600
0.900
0.800
0.800
0.800
0.700
0.600
0.600
00630
N-TOTAL
MG/L
0.460
0.550
0.450
0.550
0.580
0.710
0.680
0.020K
0.050
0.020K
006M
PMOS-; IS
OR Trie
MG/L P
0.05*
0.065
0.059
0.039
0.054
0.079
0.064
0.002K
0.006
0.003
DATE
FROM
TO
74/04/11
74/06/26
74/10/03
00665 32217 00031
TIME DEPTH PHOS-TOT CHLRPHYL INCDT LT
OF A REMNING
DAY FEET
13
13
13
14
14
14
14
14
10
10
10
50
SO
50
20
20
20
20
20
45
45
45
0000
0005
0010
0000
0003
0005
0010
0015
0000
0005
0012
MG/L P UG/L PERCENT
0
0
0
0
0
0
0
0
0
0
.252 30.7
.271
.265
.142 16.1
1.0
.160
.176
.177
.085 51.1
.104
.116
K VALUt KNOWN TO BE
LESS TH0N INDICATED
-------
APPENDIX E
TRIBUTARY AND WASTEWATER
TREATMENT PLANT DATA
-------
STORE! RETRIEVAL DATE 76/05/C4
39 04 15.0 096 52 00.0 4
20 7.5 JUNCTION CTY
0/MILFOSD *ESE^VulK . 091191
US rl«Y 77 S-DG 3 MI Nw OF JUNCTION CITY
llEPALtS 2111204
0000 FEET DEPTn CLAiS 00
DATE
FROK
TO
74/10/12
74/11/08
74/12/14
75/03/09
75/04/24
75/05/15
75/06/20
75/06/30
75/07/12
75/07/30
75/09/29
00630 0062S
TIME DEPTH N02&N03 TOT KJEL
OF N-TOTAL N
DAY FEET
09
13
09
09
13
10
08
06
09
10
09
10
30
00
00
00
00
50
00
15
00
00
MG/L
0
0
0
0
0
0
0
0
0
0
0
.312
.272
.224
.235
.035
.020
.170
.290
.140
.320
.420
HG/L
2.
1.
1.
0.
1.
0.
0.
1.
1.
0.
0.
300
800
700
900
650
650
600
450
700
850
700
00610 00671 00665
NH3-N PHOS-OIS PHOS-TOT
TOTAL GRTHO
MG/L
3.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
C90
04S
030
100
055
025
075
055
025
090
035
MG/L P
0
0
0
0
0
0
0
0
0
0
0
.040
.040
.035
.024
.015
.030
.020
.035
.020
.085
.055
MG/L P
0.065
0.140
0.100
0.040
0.040
0.080
0.040
0.050
0.050
0.14&
0.100
-------
STJPET RETRIEVAL DATE 7o/os/o<»
OATE TIME OEPTrt N02&N03
FROM Of
TO DAY FEET
7W10/12
7^/11/16
7<+/12/08
75/01/05
75/03/02
75/03/01
75/0^/13
75/OS/0<.
75/06/08
75/06/20
75/07/06
75/07/20
75/08/10
13 55
15 30
13 30
13 00
15 30
16 <»0
11 ?0
10 10
11 15
11 50
10 45
10 35
10 00
2009A2
39 21 15.0 097 08 <»5.0 <*
20 CLAY CO HWr MAP
T/Mt._FORD RESEKvOlK 091191
AT STATE H*r 15 BPuii
UE°iL£S 211120^
0000 FEET DEPTH CLASS 00
0630
AND 3
OTAL
iG/L
0.016
0.790
1.C60
1.060
0.890
1.^00
0.005
0.005
1.500
0.930
0.510
0.010
0.010
00625
TOT KJEL
N
MG/L
2.300
1.100
1.500
2.200
1.000
3.300
2.500
1.650
1.080
0.500
1.750
1.250
3.600
00610
NH3-N
TOTAL
MO/L
0.0^0
C.100
0.115
0.176
0.088
0.?92
0.035
0.025
0.035
0.1 2C
0.020
0.020
0.130
00671
PHOS-OIS
GSTriO
MG/L r
0.230
0.280
0.250
0.210
0. 168
0.22*
0.185
0.095
0.270
0.185
0.195
0.115
0.085
00665
PnOS-TOT
MG/L P
U.380
0.300
0.300
0.230
0.190
0.750
0.300
O.J20
0.510
O.S60
0.330
0.
-------
STORE! RETRIEVAL DATE 76/05/04
DATE
FROM
TO
74/10/12
74/11/16
74/12/Ofl
75/01/05
75/02/02
75/03/01
75/04/13
75/05/0<+
75/06/08
75/06/20
75/07/06
75/07/20
75/OS/10
TI«E 1
OF
DAY
13 ?5
K 05
13 45
14 15
15 45
11 00
13 50
11 00
11 30
10 20
11 00
10 00
FEET
39 21 00.0 097 12 15.0 4
FIVE CHEEKS
20 CLAY CO nwr MAP
TfMltfjPD «ES£^VO'!M 091191
AT cHOCi ON E-rf CO «D
llEPiLES 3111204
oooo FEET OE^TH CLASS oo
0630
!&N03
'OTAL
IG/L
0.112
0.200
0.083
0.096
0.200
1.375
0.230
0.220
0.500
0.390
0.180
0.1*0
0.190
00625
TOT KJEL
N
MG/L
0.800
1.500
1.600
0.500
0.400
2.900
3.300
1.750
1.400
4.000
0.550
0.950
00610
Nn3-N
TOTAL
MG/L
0.040
0.060
0.055
0.136
0.016
0.236
0.140
0.070
0.320
0.075
0.050
O.C40
0.060
00671
PriOS-OIS
OSTHO
MG/L P
0.030
0.035
0.040
0.025
0.016
0.116
0.065
0.050
0. 100
0.240
0.070
0.050
0.050
00665
PhOS-TOT
M(3/L P
0.110
0.110
0.070
0.030
0.04Q
C.330
0.140
0.120
0.330
0.160
0.090
0.160
-------
STORET RETRIEVAL DATE 76/05/04
200VC1
39 22 52.0 097 03 15.0 4
UNNAMtO STREAM
20 7.5 CL4r CcN Nv»
T/MlLFORO SESERvOI* 091191
US nwt 2<* 6RDG IN CLAV CENTER
11EJ4'-£S 211120'.
0000 FEET DEi^Tn CLASS 00
DATE
FROM
TO
74/10/12
74/1 1/16
74/12/08
75/01/05
75/02/02
75/03/01
75/04/13
75/05/04
75/06/08
75/06/20
75/07/06
75/07/19
75/08/10
75/09/06
OC630 00625
TIME DEPTH N02kN03 TOT KJEL
OF N-TuTAL N
DAY FEET
13
15
13
10
11
13
09
16
11
11
10
15
08
15
00
28
15
00
15
00
40
20
27
00
00
30
35
25
MG
C
0
0
0
0
1
0
0
1
0
0
0
0
1
XL
.016
.216
.660
.480
.624
.465
.155
.060
.570
.560
.420
.240
.430
.050
MG/L
1
1
2
1
3
4
2
1
1
0
0
0
1
0
.700
.ICO
.050 .
.200
.800
.600
.000
.450
.900
.060
.800
.750
.950
.750
00610
NM3-N *
TOTAL
MG/L
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
C40
040
045
176
032
591
055
070
POO
060
C30
017
060
C45
00671 006&5
Jn03-DIS PhOS-TOT
cm HO
MG/L
0.
0.
0.
0.
0.
0.
<).
0.
0.
0.
0.
0.
?.
p
080
045
030
015
029
432
135
085
005
155
265
250
315
MG/L P
0.165
0.140
0.070
0.050
0.070
0.730
0.230
0.130
0.230
0.010K
0.220
0.315
0.32G
0.39o
K VALUE KNOWN TO BE
LESS THAN INDICATED
-------
STOHET RETRIEVAL DATE 76/05/04
DATE TIME OEDTH N02J.N03
FROM OF
TO DAY FEET
7^/10/12
74/12/08
75/01/05
75/02/02
75/03/01
75/04/13
75/05/0^
75/06/03
75/06/20
75/07/20
75/0(4/10
75/09/06
14 30
15 30
15 30
08 52
11 10
13 45
10 00
16 35
16 15
16 30
10 10
12 30
15 10
200901
39 lo 52.0 096 59 49.0 4
MALL CHEEK
20 7.5 6ALA
T'/MiLFOSb *ESc*vO"H 091191
SEC «0 130 citfOG 3.2 MI ESE OF Br?OUGrlTON
llE-iLtb 2111204
OOOJ FEET DEPTH CLASS 00
0630
'J.N03
OTAL
IG/L
1.840
1.920
2.080
2.160
2.240
3.160
1.720
1.000
2.300
1.880
1.600
1.570
1.600
00625
TOT KJEL
N
MG/L
2.000
0.800
1.600
1.800
2.400
6.300
1.600
1.250
1.250
3.800
2.000
6.600
1.000
00610
NH3-N
TOTAL
MG/L
0.045
0.065
0.020
0.192
0.024
0.77C
0.075
0.115
0.125
0.120
0.070
0.090
0.045
00671
PhOS-DIS
ORTHO
MG/L P
0.060
0.045
0.060
0.07S
0.092
0.248
0.135
0.115
0.115
0.165
0.175
0.110
0.125
00665
PMOS-TOT
MG/L f>
0.190
0.090
0.070
0.120
0.130
0.925
0.210
0.200
0.340
0.350
0.580
0.290
0.220
-------
ST.ORET RETRIEVAL DATE 76/05/04
00630 00625 00610 00671
DATE TIME DEPTH N02J.N03 TOT KJEL Nr(3-N PhOS-OIS
FROM OF N-TOTAL N TOTAL ORTHO
TO DAY FEET MG/L MG/L MG/L MG/L P
2009F1
39 11 30.0 097 02 07.0 4
UNNAMED CREEK
20 7.5 rfA*EFI£LD
T/MILFOKD KESERVOIrJ 091191
SEC *0 BRDG 2 MI S« OF «(AKEFIELD
IIEP^LES 2111204
oooo FEET DEPTH CLASS uo
00665
PHOS-TOT
MG/L P
75/04/24 13 30
0.390
0.170
0.970
1.176
-------
STORE! RETRIEVAL DATE 76/05/04
00630 00625 00610
DATE TIME DEPTH N02J.N03 TOT KJEL NM3-N
PROM OF N-TOTAL N TOTAL
TO DAY FEET MG/L MG/L MG/L
2009G1
39 10 20.0 097 02 07.0 4
UNNAMEO CREEK
20 7.5 WAKEFIELD
T/MILFORO RESERVOIK 091191
SEC RO BRDO 3.4 MI SSW OF WAKEFIELD
11EPALES 2111204
OCOO FEET DEPTH CLASS 00 •
00665
PHOS-TOT
00671
PHOS-DIS
ORTHO
MG/L P MO/L
75/04/24 13 10
0.005
0.165
0.165
0.045
0.050
-------
STORET RETRIEVAL DATE 76/05/04
DATE TIME DEPTH N02&N03
FROM OF
TO DAY FEET
75/01/20
75/02/17
75/03/26
75/04/30
75/05/12
75/07/25
75/10/24
75/11/21
75/12/03
75/12/22
76/01/14
76/02/04
10 30
09 30
08 30
09 45
09 00
14 30
11 00
09 00
08 30
12 30
08 45
08 45
2009AA PR2009AA P000714
39 33 30.0 097 19 30.0 4
CLIFTON
20 7.5 CLIFTON
T/MILFORD RES 091191
REPUBLICAN RIVER
11EPALES 2141204
0000 FEET DEPTn CLASS 00
0630
&N03
OTAL
IG/L
0.080
0.080
0.100
0.050
0.050
0.075
0.050
0.050
0.175
0.025
1.600
00625
TOT KJEL
N
MG/L
32.500
21.000
16.000
50.000
19.000
24.000
45.000
23.000
35.000
42.500
27.000
27.000
00610
NH3-N
TOTAL
MG/L
5.300
4.300
26.300
4.600
10.000
25.000
8.900
20.000
24.000
12.000
00671
PhOS-OIS
ORTrlO
MG/L P
5.900
4.000
3.600
3.600
3.100
5.400
5.400
5.200
9.500
7.600
5.600
00665
PHOS-TOT
MG/L P
8.100
6.000
5.600
12.500
5.500
11.500
10.000
7.000
13.500
8.450
9.400
10.000
50051
FLOW
RATE
INST MGD
0.100
0.075
0.070
0.074
0.068
0.071
0.072
0.087
0.075
0.096
0.078
50053
CONDUIT
FLOW-MGD
MONTHLY
0.100
0.077
0.080
0.078
0.092
Oo068
0.071
0.072
0.084
0.071
0.095
0.078
-------
STORET RETRIEVAL DATE 76/05/04
DATE
FROM
TO
75/01/06
CP < T > -
75/01/06
75/02/04
CP(T)-
75/02/04
75/03/04
CP(T>-
75/03/04
75/04/07
CP(T)-
75/04/07
75/05/06
CP(T>-
75/05/06
75/06/03
75/07/14
CP(T)-
75/07/14
75/08/03
CP
-------
STORE! RETRIEVAL DATE 76/05/04
00630 00625
DATE TIME DEPTH N02&N03 TOT KJEL
FROM OF N-TOTAL N
TO DAY FEET MG/L MG/L
75/02/18 11 00
CP < T > -
75/02/18 16 00
75/03/16 08 00
CP(T)-
75/03/16 16 00
75/04/15 08 00
CP-
75/04/15 16 00
75/05/06 08 00
CP-
75/05/06 17 00
75/05/27 09 00
CP(T)-
75/05/27 16 00
75/06/17 08 00
CP(T)-
75/06/17 15 00
75/07/08 08 00
CP(T>-
75/07/08 17 00
75/07/29 07 00
CP-
75/07/29 17 00
75/08/19 08 00
CP-
75/08/19 18 00
75/09/09 08 00
CP(T)-
75/09/09 17 00
75/09/30 08 00
CP(T)-
75/09/30 17 00
75/10/21 08 00
CP(T)-
75/10/21 17 00
2009AC PR2009AC P0050^3
39 21 40.0 097 07 30.0 4
CLAY CENTER
20 7.5 CLAY CENTER
T/MILFORO RESERVGIK 091191
REPUBLICAN RIVER
UEPALES 2141204
0000 FEET DEPTH CLASS 00
00610 00671 00665 50051 50053
NH3-N PHOS-OIS PHOS-TOT FLOW CONDUIT
TOTAL ORTHO RATE FLOW-MGD
MG/L MG/L P MG/L P INST MOD MONTHLY
0.005
0.880
0.320
0.050
0.350
1.050
0.150
2.750
1.450
1.570
1.950
0.025
0.275
21.000
18.000
19.500
16.500
16.000
16.500
9.700
8.200
11.000
9.200
19.000
21.000
8.100
11.600
10.000
4.300
4.700
4.900
0.140
0.450
0.200
6.400
8.300
2.800
5.000
3.300
2.900
3.200
0.900
1.720
2.300
2.100
2.100
4.300
4.100
5.200
6.000
5.600
5.100
3.700
4.800
2.800
2.900
3.300
2.900
5.800
5.800
-------
STORET RETRIEVAL DATE 76/05/04
00630
DATE TIME DEPTH N02^N03
FROM OF N-TOTAL
TO DAY FEET MG/L
75/11/16 08 00
CP(T>-
75/11/16 16 00
0.075
34.000
2009AC Ph!2009AC
39 21 40.0 097 07 30.0 4
CLAY CENTER
20 7.5 CLAY CENTEW
T/MILFO'RD RESEKVOiS
REPUBLICAN RIVER
IIE^ALES 2141204
0000 FEET DEPTrt CLASS 00
PQ05093
00625
TOT KJEL
N
MG/L
00610
NH3-N
TOTAL
MG/L
00671
PhOS-OIS
ORTHO
MG/L P
00665
PHOS-TOT
MG/L P
50051
FLOW
RATE
INST MGO
50053
CONDUIT
FLOW-MGO
MONTHLY
10.500
5.000
9.800
-------
STORET RETRIEVAL DATE 76X05/04
DATE TIME DEPTH N02&N03
FROM OF
TO DAY FEET
75/02/10
75/03/12
75/04/11
75/04/29
75/05/19
75/06/04
75/06/30
75/07/29
75/09/24
75/10/20
75/11/06
75/12/02
75/12/22
15 35
16 40
14 25
15 15
14 00
00 00
15 00
16 10
00 00
2009AD P02009AD P000963
39 35 00.0 097 24 00.0 4
CLYDE
20 7.5 CLYDE
T/MILFORD RESERVOIR 091191
REPUBLICAN RIVER
11EPALES 2141204
0000 FEET DEPTH CLASS 00
0630
'{.N03
OTAL
IG/L
0.160
0.160
1.200
0.050
0.150
0.150
0.025
0.025
0.050
0.425
0.675
0.950
1.200
00625
TOT KJEL
N
MG/L
3.000
7.000
21.000
22.000
30.000
18.000
9.000
11.500
11.500
8.200
9.100
6.300
7.700
00610
NH3-N
TOTAL
MG/L
1.550
5.900
8.000
0.290
1.250
0.120
0.025K
0.175
0.035
0.025K
0.200
0.250
00671
PMOS-DIS
ORTHO
MG/L P
6.530
6.000
7.400
7.900
9.400
7.030
2.100
3.800
4.175
4.500
4.300
5.700
00665
PHOS-TOT
MG/L P
7.080
6.900
8.100
9.200
9.400
10.200
7.300
2.500
4.800
5.200
5.700
5.400
6.400
50051
FLOW
HATE
INST MOD
0.100
0.150
0.150
0.160
0.300
0.100
0.150
0.120
0.144
50053
CONDUIT
FLOW-MGD
MONTHLY
0.150
0.115
0.250
0.100
0.130
0.125
0.129
K VALUE KNOWN TO BE
LESS THAN INDICATED
-------
STORET RETRIEVAL DATE 76/05/04
DATE TIME DEPTH N02&N03
FROM OF
TO DAY FEET
75/03/06
75/04/03"
75/05/01
75/05/23
75/06/12
75/07/07
75/07/24
75/08/07
75/09/28
75/09/18
75/10/19
75/10/29
11
11
11
11
11
11
11
11
11
11
11
11
IS
30
00
30
30
30
30
30
30
30
30
30
20C9AE P02009AE P007680
39 34 40.0 097 38 00.0 4
CONCORD I A
20 7.5 COHCORDIA
T/MILFORO RES. 091191
REPUBLICAN RIVER
HEPALES 2141204
0000 FEET DEPTH CLASS 00
0630
&N03
OTAL
G/L
0.160
0.240
0.050
0.050
0.050
0.025
0.050
0.100
0.075
0.025
0.075
0.025
00625
TOT KJEL
N
MG/L
53.000
45.000
65.000
46.000
48.300
28.000
37.000
33.000
40.000
47.000
48.000
46.000
00610
NH3-N
TOTAL
MG/L
22.000
18.400
25.000
22.500
19.950
14.000
14.500
13.500
17.500
24.000
26.500
24.500
00671
PHOS-DIS
ORTHO
MG/L P
5.520
4.900
3.200
4.000
3.800
6.100
^.SOO
2.500
7.800
8.800
3.200
4.400
00665
PHOS-TOT
MG/L P
17.500
14.500
19.500
16.000
15.500
9.200
5.700
13.000
12.800
11.000
25.000
16.500
50051
FLOW
RATE
INST MGD
0.266
0.300
0.246
0.202
0.222
0.518
0.270
0.300
50053
CONDUIT
FLOW-MOD
MONTHLY
0.272
0.300
0.225
0.200
0.211
0.500
0.265
0.275
-------
STOPET RETRIEVAL DATE 76/07/12
00630
DATE TIME DEPTH N02&N03
FROM OF N-TOTAL
TO OAY FEET MG/L
75/04/24 13 30
0.390
2009F1
39 11 30.0 097 02 07.0 4
UNNAMED CREEK
20 7.5 WAKEFIELD
T/MILFORD RESERVOIR 091191
SEC RO BRDG 2 MI SW OF WAKEFIELD
11EPALES 2111204
0000 FEET DEPTH CLASS 00
00625
TOT KJEL
N
MG/L
00610
NH3-N
TOTAL
MG/L
0.170
00671
PHOS-DIS
ORTHO
MG/L P
0.970
00665
PHOS-TOT
MG/L P
1.176
50051
FLOW
RATE
INST MGD
50053
CONDUIT
FLOX-MGD
MONTHLY
------- |