U.S. ENVIRONMENTAL PROTECTION AGENCY
NATIONAL EUTROPHICATION SURVEY
WORKING PAPER SERIES
REPORT
ON
PERRY RESERVOIR
JEFFERSON COUNTY
KANSAS
EPA REGION VII
WORKING PAPER No, 521
CORVALLIS ENVIRONMENTAL RESEARCH LABORATORY - CORVALLIS, OREGON
and
ENVIRONMENTAL MONITORING & SUPPORT LABORATORY - LAS VEGAS, NEVADA
TwTG.P.O. 699-440
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REPORT
ON
PERRY RESERVOIR
JEFFERSON COUNTY
KANSAS
EPA REGION VII
WORKING PAPER No, 521
WITH THE COOPERATION OF THE
KANSAS DEPARTMENT OF HEALTH AND ENVIRONMENT
AND THE
KANSAS NATIONAL GUARD
MAY, 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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ii
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.
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Ill
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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1v
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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LSobetho
Kan.
Map Location
WetmoreX
-v'^
) N- LKt,ncroh " ^
\ N N v
PERRY RESERVOIR
® Tributary Sampling Site
X I aki.' Jamplinq Site
^ Sewage Treatment Facility
10 Drainage Area Boundary
Land Subject to Inundation
»o Km.
Sc
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PERRY RESERVOIR
STORE! NO. 2011
I. CONCLUSIONS
A. Trophic Condition:
Survey data indicate that Perry 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 ninth in overall trophic quality
when the 15 Kansas reservoirs sampled in 1974 were compared
using a combination of six water quality parameters*. Seven
of the reservoirs had less median total phosphorus, eight had
less median dissolved orthophosphorus, 11 had less and one had
the same median inorganic nitrogen, two had less mean chlorophyll
£, and six had greater mean Secchi disc transparency. Depression
of dissolved oxygen with depth occurred at all sampling stations
in June.
Survey limnologists did not observe any nuisance conditions
during their sampling but did note that the reservoir was quite
turbid at times.
B. Rate-Limiting Nutrient:
The algal assay results indicate that Perry Reservoir was
phosphorus limited at the time the sample was collected (02/12/74),
See Appendix A.
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The reservoir data indicate phosphorus limitation at all
sampling stations and times. However, because of turbidity,
primary productivity in the reservoir is intermittently light-
limited rather than nutrient-limited.
C. Nutrient Controllability:
1. Point sources--During the sampling year, the listed
point sources accounted for 18.0% of the total phosphorus load to
Perry Reservoir. The wastewater treatment plant at Morton con-
tributed 7.4%, the facility at Holton contributed 7.2%, the plant
at Wetmore contributed 0.4%, and the remaining four plants were
estimated to have collectively contributed 3.0%.
The present phosphorus loading of 2.07 g/m2/year is 4.7
times that proposed by Vollenweider (Vollenweider and Dillon,
1974) as a eutrophic loading (see page 15). Even though nutrient-
wise the reservoir is phosphorus-limited, reduction of the point-
source phosphorus loads may not result in a significant improve-
ment of the trophic condition because of light-limitation. In
a previous report it is noted that while nutrient levels in
Perry Reservoir are high, aquatic growths are not excessive due
to high turbidity resulting from soil erosion in the drainage
of the reservoir (Anonymous, 1975). However, if soil conservation
projects are initiated to reduce erosion and the resulting tur-
bidity in the reservoir, the present phosphorus loading is likely
to result in the development of nuisance aquatic vegetation.
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2. Non-point sources--Non-point sources contributed 82.0%
of the total phosphorus load during the sampling year. The
Delaware River contributed 71.0%, Slough Creek contributed 1.3%,
Little Slough Creek contributed 0.4%, and Rock Creek contributed
0.8%. Ungaged minor tributaries and immediate drainage contributed
an estimated 7.6%.
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II. RESERVOIR AND DRAINAGE BASIN CHARACTERISTICS1"
A. Morphometry :
1. Surface area: 49.37 kilometers2.
2. Mean depth: 3.7 meters.
3. Maximum depth: 11.9 meters.
4. Volume: 182.669 x 106 m3.
5. Five-year median hydraulic retention time: 281 days.
B. Tributary and Outlet:
(See Appendix C for flow data)
1. Tributaries -
Drainage Mean flow
Name area (km2)* (m3/sec)*
Delaware River (at A-3) 1,942.5 9.110
Slough Creek 109.8 0.650
Little Slough Creek 47.1 0.088
Rock Creek (at E-2) 35.5 0.200
Minor tributaries &
immediate drainage - 708.7 3.472
Totals 2,843.6 13.520**
2. Outlet -
Delaware River 2,893.0*** 12.710
C. Precipitation****:
1. Year of sampling: 75.3 centimeters.
2. Mean annual: 92.4 centimeters.
t Table of metric conversions—Appendix B.
tt Kring, 1977.
* For limits of accuracy, see Working Paper No. 175, "...Survey Methods,
1973-1976".
** Total inflow adjusted to equal outflow plus evaporation loss.
*** Includes area of reservoir.
**** See Working Paper No. 175.
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III. WATER QUALITY SUMMARY
Perry 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 in April and five stations
in June and October (see map, page v). During each visit, a single
depth-integrated (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
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PARAMETER
TEMP (C)
DISS OXY (MG/L)
CNOCTVY (MCROMO)
PH (STAND UNITS)
TOT ALK (MG/L)
TOT P (MG/L)
ORTHO P (MG/L)
N02+N03 (MG/L)
AMMONIA (MG/D
KJEL N (MG/L)
INORG N (MG/L)
TOTAL N (MG/L)
CHLRPYL A (UG/L)
SECCHI (METERS)
A. SUMMARY OF PHYSICAL AND
1ST SAMPLING ( 4/12/74)
4 SITES
RANGE MEAN MEDIAN
10.0 - 11.7 10.7 10.6
9.2 - 10.4 9.9 10.0
8.3
167.
0.037
0.008
0.450
0.040
0.400
0.580
1.060
5.1
0.5
8.4
- 204.
- 0.064
- 0.035
- 1.140
- 0.130
- 0.800
- 1.220
- 1.640
- 13.2
0.8
8.3
178.
0.053
0.020
0.849
0.082
0.572
0.931
1.422
8.7
0.6
8.3
174.
0.056
0.017
0.905
0.075
0.600
0.975
1.450
8.3
0.6
CHEMICAL CHARACTERISTICS FOR PERRY RESERVOIR
STORE? CODE 2011
2ND SAMPLING ( 6/25/74)
5 SITES
RANGE
19.9 - 26.8
1.6 - 14.2
371. - 423.
7.9 - 8.7
142. - 171.
0.032 - 0.149
0.011 - 0.051
0.850 - 1.960
0.040 - 0.190
0.300 - 0.300
0.920 - 2.070
1.250 - 2.440
0.9 - 4.9
0.3 - 0.6
3RD SAMPLING (10/ 2/74)
5 SITES
MEAN
23.2
5.2
395.
6.2
161.
0.074
0.026
1.372
0.077
0.443
1.449
1.816
2.9
0.5
MEDIAN
23.3
5.4
396.
8.2
161.
0.064
0.022
1.250
0.070
0.400
1.300
1.660
2.9
0.6
RANGE
15.9
7.8
167.
7.8
162.
0.035
0.011
0.540
0.020
0.200
0.600
1.040
1.9
0.5
- 17.6
9.0
- 337.
8.2
- 172.
- 0.096
- 0.020
- 0.880
- 0.060
- 0.900
- 0.910
- 1.530
- 12.8
0.7
MEAN
17.0
8.3
317.
8.1
165.
0.052
0.015
0.768
0.033
0.445
0.801
1.213
5.8
0.5
MEDIAN
17.2
8.4
331.
8.1
164.
0.049
0.015
0.800
0.030
0.450
0.830
1.200
5.2
0.5
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B. Biological Characteristics:
1. Phytoplankton -
Sampling
Date
04/12/74
06/25/74
10/02/74
Dominant
Genera
1.
2.
3.
4.
5.
1.
2.
3.
4.
5.
1.
2.
3.
4.
5.
Stephanodiscus sp.
Chroomonas sp.
Melosira sp.
Cryptomonas sp.
Chlorococcol cells
Other genera
Total
Cryptomonas sp.
Flagellates
Trachelomonas sp.
Chroomonas sp.
Coelastrum sp.
Other genera
Total
Chroomonas sp.
Melosira sp^.
Nitzschia sp.
Cryptomonas sp.
Skeletonema sp.
Other genera
Algal Units
per ml
891
806
806
127
127
338
Total
3,095
368
221
184
147
37
146
1,103
741
456
456
285
114
341
2,393
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8
C.
Sampling
Date
04/12/74
06/25/74
10/02/74
Dominant
Genera
1
2
3
4
5
1
2
3
4
5
1
2
3
4
5
Chlorophyll a
(ug/D
5.1
13.2
9.6
7.1
4.3
4.9
1.5
0.9
2.9
3.0
5.2
6.2
12.8
1.9
Limiting Nutrient Study:
1.
2.
Autoclaved, filtered,
Ortho
Spike (mg/1) Cone.
Control 0.
0.050 P 0.
0.050 P + 1.0 N 0.
1.0 N 0.
Discussion -
The control yield
and nutrient spiked -
P Inorganic N
(mg/1) Cone, (mg/1)
010 0.791
060 0.791
060 1.791
010 1.791
Maximum yield
(mg/1 -dry wt. )
7.4
25.0
34.9
6.5
of the assay alga, Selenastrum capri-
cornutum, indicates that the potential primary
productivity
of Perry Reservoir was high at the time the sample was col-
lected (04/12/74). Also, the increase in yield with the
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addition of phosphorus alone indicates that the reservoir
was phosphorus limited at that time. Note that the addition
of nitrogen alone resulted in a yield no greater than that
of the control.
The reservoir data also indicate phosphorus limitation.
The mean inorganic nitrogen/orthophosphorus ratios were 36/1
or greater at all sampling stations and times, and phosphorus
limitation would be expected. However, primary productivity
in the reservoir is intermittently light-limited rather than
nutrient-limited (Kring, 1977).
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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 map (page v), except for the months
of May, 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
calculated using mean annual concentrations and mean annual flows.
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 mean concen-
trations in Brush Creek at station D-l and the mean annual ZZ flow.
The operators of the Everest, Hoi ton, Morton, and Wetmore waste-
water treatment plants provided monthly effluent samples and corres-
ponding flow data. The operators of the wastewater treatment plants
of Denison, Oskaloosa, and Valley Falls did not participate; nutrient
loads from these sources were estimated at 1.134 kg P and 3.401 kg
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11
N/capita/year, and flows were estimated at 0.3785 m3/capita/day.
A. Waste Sources:
1. Known municipal* -
Name
Denison
Everest
Hoi ton
Morton
Oskaloosa
Valley Falls
Wetmore
2. Known industrial -
Name
Meat Packing Plant,
Hoi ton**
Pop.
Served
278
359
3,369
2,385
1,005
1,291
415
Treatment
stab, pond
stab, pond
tr. filter
tr. filter
stab, pond
stab, pond
tr. filter
Mean Flow
(ms/d)
105.2
113.1
1,817.7
2,205.9
380.4
488.6
98.3
Receiving
Water
North Cedar Creek
Grasshopper Creek
Elks Creek
Delaware River
Big Slough Creek
Delaware River
Spring Creek
Treatment
Mean Flow
(m3/d)
anaerobic -
aerobic ponds
Receiving
Water
Elks Creek
* Treatment plant questionnaires.
** Not in operation during the sampling year.
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12
B. Annual Total Phosphorus Loading - Average Year:
1. Inputs -
kg P/ % of
Source yr total
a. Tributaries (non-point load) -
Delaware River (A-3) 72,665 71.0
Slough Creek 1,360 1.3
Little Slough Creek 455 0.4
Rock Creek (E-2) 775 0.8
b. Minor tributaries & immediate
drainage (non-point load) - 7,775 7.6
c. Known municipal STP's -
Denison 315 0.3
Everest 165 0.2
Holton 7,385 7.2
Horton 7,615 7.4
Oskaloosa 1,140 1.1
Valley Falls 1,465 1.4
Wetmore 370 0.4
d. Septic tanks - Unknown ?
e. Known industrial - None
f. Direct precipitation* - 865 0.9
Total 102,350 100.0
2. Outputs -
Reservoir outlet - Delaware River 24,850
3. Net annual P accumulation - 77,500 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) -
Delaware River (A-3) 473,270 60.9
Slough Creek 24,520 3.2
Little Slough Creek 5,325 0.7
Rock Creek (E-2) 10,695 1.4
b. Minor tributaries & immediate
drainage (non-point load) - 172,670 22.2
c. Known municipal STP's -
Denison 945 0.1
Everest 360 <0.1
Hoi ton 11,395 1.5
Horton 16,110 2.1
Oskaloosa 3,420 0.4
Valley Falls 4,390 0.6
Wetmore 480 <0.1
d. Septic tanks - Unknown ?
e. Known industrial - None
f. Direct precipitation* - 53,300 6.9
Total 776,870 100.0
2. Outputs -
Reservoir outlet - Delaware River 515,860
3. Net annual N accumulation - 261,010 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
Delaware River (A-3) 37 244
Slough Creek 12 223
Little Slough Creek 32 375
Rock Creek (E-2) 22 301
E. Mean Nutrient Concentrations in Ungaged Streams:
Mean Total P Mean Total N
Tributary Cone, (mg/1) Cone, (mg/1)
Brush Creek 0.071 1.577
Evans Creek 0.066 0.817
Fishpond Creek 0.139 2.279
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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.
Total Phosphorus Total Nitrogen
Total Accumulated Total Accumulated
grams/m2/yr 2.07 1.57 15.7 5.3
Vollenweider phosphorus loadings
(g/m2/yr) based on mean depth and 5-year median
hydraulic retention time of Perry Reservoir:
"Dangerous" (eutrophic loading) 0.44
"Permissible" (oligotrophic loading) 0.22
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16
V. LITERATURE REVIEWED
Anonymous, 1975. Final environmental statement: Operation and
maintenance, Perry Lake, Kansas. U.S. Army Engr. Distr.,
Kansas City, MO.
Kring, R. Lynn, 1977. Personal communication (revised reservoir
morphometry; primary productivity). 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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17
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
2002 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
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
12.8CO
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 BY 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
200fl MELVERN RESERVOIR
2009 MILFORO 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 1
7 1
50 1
71 1
36 (
0 i
93 1
: 14)
: 4)
; 12)
: e>
: 2)
: 6)
: 9)
, ID
: 3)
! 1)
1 7)
1 10)
1 5)
I 0)
1 13)
MEDIAN
INORG N
100 (
29 (
50 (
57 (
0 (
43 <
64 <
82 <
36 <
93 1
18 <
.7 1
71 i
18 i
82 <
: 14)
! 4)
: 7)
: a)
: o)
: 6>
[ 9)
t ID
[ 5)
I 13)
! 2)
t 1)
I 10)
t 2)
I 11)
500-
MEAN SEC
100 <
36 (
7 1
14 (
0 1
29 1
43 (
86 1
79 1
64 1
57 (
50 i
21 i
71 i
93 i
: 14)
: 5)
: i)
; 2)
: o)
: 4)
[ 6)
[ 12)
[ 11)
: 9)
[ 3)
[ 7)
t 3)
( 10)
( 13)
MEAN
CHLORA
93 (
43 (
100 <
71 I
50 <
21 <
29 1
0 <
14 1
7 1
86 1
64 I
79 i
36 i
57 i
: 13)
: 6)
: 14)
: 10)
; 7)
: 3)
i 4)
: o>
: 2>
i i>
[ 12)
[ 9)
[ 11)
( 5)
[ 8)
15-
MIN DO
57 <
64 (
7 <
79 <
93 (
71 (
86 (
0 (
50 <
100 1
25 1
39 1
39 i
14 i
25 i
: e)
9)
1)
: 11)
; 13)
: io>
; 12)
1 0)
I 7)
[ 14)
[ 3)
! 5)
: 5)
( 2)
: 3)
MEDIAN
DISS OftTHO P
89 (
29 <
100 <
50 (
7 (
64 (
71 1
79 1
14 1
21 1
43 I
36 (
57 i
0 i
89 i
L2)
4)
: 14)
; 7)
: i)
: 9)
: 10)
; ID
[ 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
-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
1.2/0376
LA
-------
TRIBUTARY FLOW INFORMATION FOR KANSAS
12/0376
LAKE CODE 2011
PERRY
MEAN MONTHLY FLOWS AND GAILY FLOWS(CMS)
TRIBUTARY MONTh YEAR
2011B1
2011C1
2011E2
2011ZZ
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
10
11
12
1
2
3
i»
5
6
7
8
9
74
7*.
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 FLOW DAY
0.037
0.054
0.065
0.108
0.368
0.396
0.680
0.991
2.407
0.096
0.022
0.059
0.005
0.007
0.010
0.016
0.048
0.068
0.088
0.142
0.272
0.014
0.003
0.006
0.012
0.016
0.020
0.034
0.108
0.142
0.193
0.311
0.680
0.031
0.007
0.016
0.283
0.510
0.481
0.793
2.549
2.350
5.097
7.646
21.238
0.708
0.311
0.595
12
9
14
13
6
9
13
11
7
13
10
7
12
9
It
11
8
9
13
11
7
13
10
7
12
9
14
11
8
8
11
11
7
13
10
7
FLOW DAY
FLOW DAY
FLOW
0.651
0.481
0.340
0.566
0.510
0.368
0.510
0.340
0.255
0.042
0.003
0.085
0.042
0.071
0.048
0.057
0.057
0.0
0.071
0.042
0.011
0.006
0.0
0.0
0.008
0.014
0.014
0.014
0.028
0.017
0.076
0.065
0.062
0.008
0.001
O.OC1
24
21
27
24
21
27
24
21
27
0.991
0.566
0.014
0.074
0.068
0.003
0.025
0.057
0.008
-------
APPENDIX D
PHYSICAL and CHEMICAL DATA
-------
STORE! RETRIEVAL DATE 76/05/03
201101
39 06 52.0 095 25 40.0 3
PERRY RESERVOIR
20087 KANSAS
091191
11EPALES 2111202
0050 FEET DEPTH CLASS 00
DATE
FROM
TO
74/04/12
74/06/25
74/10/02
00010
TIME DEPTH WATER
OF TEMP
DAY FEET CENT
10 00
10 00
10 00
10 00
10 00
15 40
15 40
15 40
15 40
15 40
15 40
12 00
12 00
12 00
12 00
12 00
0000
0005
0015
0030
0040
0000
0005
0015
0030
0040
0050
0000
0005
0020
0035
0050
10.0
10.0
10.0
10.0
10.0
26.7
26.8
23.3
23.0
20.6
19.9
17.6
17.6
17.5
17.5
17.5
00300 00077 00094
DO TRANSP CNDUCTVY
SECCHI FIELD
MG/L INCHES MICROMHO
10.0
10.0
10.4
10.0
14.2
6.0
7.2
6.4
2.8
2.2
8.0
8.0
8.2
8.2
8.0
32
24 422
423
399
396
379
371
26 333
337
335
333
335
00400 00410
PH T ALK
CAC03
SU MG/L
8.40
8.40
8.35
8. 35
8.30
8.70
8.60
8.30
8.20
7.90
7.90
8.09
8.13
8.11
8.11
8.09
168
171
168
168
167
160
160
160
161
162
163
164
163
164
162
163
00610 00625 00630 00671
NH3-N TOT KJEL N02&N03 PHOS-DIS
TOTAL N N-TOTAL ORTHO
MG/L MG/L MG/L MG/L P
0.070
0.080
0.070
0.080
0.080
0.040
0.050
0.060
0.050
0.050
0.040
0.030
0.030
0.040
0.020
0.020
0.500
0.500
0.400
0.500
0.400
0.600
0.400
0.400
0.400
0.400
0.400
0.400
0.200
0.200K
0.200K
0.300
1.130
1.140
1.140
1.140
1.130
1.180
1. 170
1. 140
1.030
1.250
1.210
0.870
0.880
0.870
0.860
0.860
0.031
0.035
0.034
0.034
0.035
0.015
0. 0?1
. V C. I
0.021
O.OP?
. w a c.
0.036
0.018
0.018
0.017
0.017
0.017
DATE
FROM
TO
74/04/12
74/06/25
74/10/02
TIME DEPTH
OF
DAY FEET
10 00 0000
10 00 0005
10 00 0015
10 00 0030
10 00 0040
15 40 0000
15 40 0005
15 40 0015
15 40 0030
15 40 0040
15 40 0050
12 00 0000
12 00 0005
12 00 0020
12 00 0035
12 00 0050
00665
PHOS-TOT
MG/L P
0.059
0.057
0.061
0.056
0.056
0.032
0.036
0.032
0.035
0.086
0.042
0.038
0.038
0.038
0.035
0.098
32217 00031
CHLRPHYL INCDT LT
A REMNING
UG/L PERCENT
5.1
4.3
3.0
1.0
K VALUE KNOWN TO BE
LESS THAN INDICATED
-------
STORET RETRIEVAL DATE 76/05/03
201102
39 08 37.0 095 24 12.0 3
PERRY RESERVOIR
20037 KANSAS
091191
DATE
FROM
TO
74/04/12
74/06/26
74/10/02
DATE
FROM
TO
74/04/12
74/06/26
74/10/02
TIME DEPTH
OF
DAY FEET
12 15 0000
12 15 0005
12 15 0015
12 15 0030
10 05 0000
10 05 0005
10 05 0015
10 05 0027
11 35 0000
11 35 0005
11 35 0015
11 35 0028
TIME DEPTH
OF
DAY FEET
12 15 0000
12 15 0005
12 15 0015
12 15 0030
10 05 0000
10 05 0005
10 05 0006
10 05 0015
10 05 0027
11 35 0000
11 35 0005
11 35 0015
11 35 0028
00010
WATER
TEMP
CENT
11.0
11.0
10.9
10.8
23.4
23.2
23.0
22.0
17.2
17.2
17.2
17.2
00665
PHOS-TOT
MG/L P
0.063
0.059
0.063
0.064
0.059
0.043
0.053
0.092
0.048
0.049
0.046
0.062
11EPALES 2111202
0035 FEET DEPTH CLASS 00
00300 00077 00094 00400 00410 00610 00625 00630 00671
DO TRANSP CNDUCTVY PH T ALK NH3-N TOT KJEL N02&N03 PHOS-DIS
SECCHI FIELD CAC03 TOTAL N N-TOTAL OWTHO
MG/L
9.
10.
10.
6.
6.
6.
1.
8.
8.
8.
7.
32217
INCHES MICROMHO SU
25
8
0
0
8 24
8
4
6
2 18
4
0
8
00031
8.
8.
8.
8.
399 8.
398 8.
398 8.
399 7.
331 8.
329 8.
331 8.
333 8.
40
35
30
30
40
30
20
90
09
13
13
11
MG/L
172
173
170
170
165
167
164
171
164
163
164
164
MG/L
0.050
0.040
0.040
0.060
0.090
0.070
0.090
0.090
0.030
0.020
0.030
0.040
MG/L
0.600
0.500
0.600
0.600
0.600
0.400
0.400
0.400
0.400
0.500
0.500
0.500
MG/L
0.780
0.760
0.780
0.880
1.000
0.850
1.030
1.200
0.800
0.810
0.820
0.820
MG/L P
0.018
0.017
0.018
0.022
0.011
0.012
0.016
0.017
0.015
0.015
0.016
0.016
CHLRPHYL INCDT LT
A
UG/L
13.
4.
5.
REMNING
PERCENT
2
9
1.0
2
-------
STORET RETRIEVAL DATE 76/05/03
201103
39 09 53.0 095 27 33.0 3
PERRY RESERVOIR
20087 KANSAS
091191
DATE
FROM
TO
74/04/12
74/06/26
74/ 10/02
DATE
FROM
TO
74/04/12
74/06/26
74/10/02
TIME DEPTH
OF
DAY FEET
12 40 0000
12 40 0005
12 40 0015
12 40 0030
12 40 0045
10 30 0000
10 30 0005
10 30 0015
10 30 0030
10 30 0044
10 25 0000
10 25 0005
10 25 0015
10 25 0030
10 ?5 0044
TIME DEPTH
OF
DAY FEET
12 40 0000
12 40 0005
12 40 0015
12 40 0030
12 40 0045
10 30 0000
10 30 0005
10 30 0006
10 30 0015
10 30 0030
10 30 0044
10 25 0000
10 25 0005
10 25 0015
10 25 0030
10 25 0044
00010
WATER
TEMP
CENT
10.7
10.5
10.5
10.5
10.5
23.5
23. S
23.0
22.2
21.0
17.3
17.3
17.3
17.3
17.3
00665
PHOS-TOT
MG/L P
0.049
0.045
0.048
0.048
9.043
0.079
0.05S
0.049
0.080
0.095
0.044
0.044
0.055
0.055
0.067
00300 00077
DO TRANSP
MG/L
10.
10.
10.
10.
2.
S.
5.
3.
2.
8.
9.
B.
8.
8.
32217
SECCHI
INCHES
24
0
0
2
2
0 12
4
4
8
4
4 18
0
4
4
4
00031
00094
CNDUCTVY
FIELD
MICROMHO
392
393
395
394
387
327
335
335
333
331
11EPALES 2111202
0050 FEET DEPTH CLASS 00
00400 00410 00610 00625
PH T ALK NH3-N TOT KJEL
SU
8.40
8.40
8.35
8.35
8.35
8.30
8.20
8.10
8.00
8.00
8.09
8.19
8.19
8.07
8.11
CAC03
MG/L
174
174
175
174
174
160
159
164
166
170
169
168
166
165
166
TOTAL
MG/L
0.080
0.090
0.070
0.070
0.070
0.050
0.080
0.050
0.080
0.070
0.030
0.040
0.030
0.030
0.020
N
MG/L
0.700
0.500
0.500
0.600
0.600
0.400
0.400
0.300
0.300
0.400
0.600
0.400
0.500
0.400
0.400
00630
N02&N03
N-TOTAL
MG/L
0.920
0.920
0.910
0.910
0.900
1.900
1.950
1.510
1.630
1.640
0.790
0.800
0.800
0.800
0.780
00671
PHOS-DIS
ORTHO
MG/L P
0.016
0.016
0.016
0.016
0.021
0.029
0.027
0.022
0.022
0.021
0.015
0.016
0.016
0.016
0.020
CHLRPHYL INCOT LT
A
UG/L
9.
1.
6.
REMNING
PERCENT
6
5
1.0
2
-------
STORET RETRIEVAL DATE 76/05/03
201104
39 13 43.0 095 27 23.0 3
PERRY RESERVOIR
20037 KANSAS
091191
UEPALES 2111202 .
0035 FEET DEPTH CLASS 00
DATE
FROM
TO
74/04/12
74/06/26
74/10/04
DATE
FROM
TO
74/04/12
74/06/26
74/10/04
TIME
OF
DAY
13 15
13 15
13 15
13 15
11 00
11 00
11 00
11 00
09 55
09 55
09 55
09 55
TIME
OF
DAY
13 15
13 15
13 15
13 15
11 00
11 00
11 00
11 00
11 00
09 55
09 55
09 55
09 55
09 55
DEPTH
FEET
0000
0005
0015
0030
0000
0005
0015
0027
0000
0005
0015
0028
DEPTH
FEET
0000
0005
0015
0030
0000
0003
0005
0015
0027
0000
0003
0005
0015
0026
00010
WATER
TEMP
CENT
11.7
11.7
11.6
11.5
23.5
23.4
23.3
22.2
16.3
16.2
16.1
15.9
00665
PHOS-TOT
MG/L P
0.037
0.045
0.049
0.057
0.121
0.117
0.133
0.116
0.052
0.052
0.059
0.064
00300 00077 00094 00400 00410
00 TRANSP CNOUCTVY PH T ALK
SECCH1 FIELD CAC03
MG/L INCHES MICROMHO SU MG/L
20
9.4
9.2
9.2
5.4 12
5.0
4.8
3.2
8.4 18
8.6
8.8
8.4
32217 00031
CHLRPHYL INCDT LT
A REMNING
UG/L PERCENT
7.1
0.9
1.0
12.8
1.0
8
8
8
8
376 8
376 8
382 8
393 8
167 7
267 8
279 7
279 7
.30
.30
.30
.30
.20
.10
.00
.00
.75
.05
.99
.91
204
202
203
201
142
148
147
159
167
168
170
172
00610 00625 00630 00671
NH3-N TOT KJEL N02&N03 PHOS-DIS
TOTAL N N-TOTAL ORTHO
MG/L MG/L MG/L MG/L P
0.130
0.130
0.130
0.130
0.090
0.130
0.080
0.080
0.050
Oe040
Oo060
0.060
0.800
0.600
0.700
0.700
0.400
0.500
0.500
0.400
0.900
0.600
0.600
0.500
0.460
0.460
0.450
0.480
1.960
1.940
1.800
1.560
0.630
0.580
0.560
0.540
0.010
0.009
0.008
0.009
0.051
0.050
0.043
0.029
0.015
0.012
0.011
0.011
-------
STORET RETRIEVAL DATE 76/05/03
301105
39 09 00.0 095 28 53.0 3
PERRY RESERVOIR
20 KANSAS
091191
11EPALES
2111202
0033 FEET DEPTH CLASS
DATE
FROM
TO
74/06/36
74/10/02
DATE
FROM
TO
74/06/36
74/10/02
TIME DEPTH
OF
DAY FEET
09 40 0000
09 40 0005
09 40 0015
09 40 0037
11 00 0000
11 00 0005
11 00 0015
11 00 0024
TIME DEPTH
OF
DAY FEET
09 40 0000
09 40 0005
09 40 0015
09 40 0027
11 00 0000
11 00 0001
11 00 0004
11 00 0005
11 00 0015
11 00 0024
00010
HATER
TEMP
CENT
24.4
24.3
23.8
22.6
16.9
16.9
16.8
16.5
00665
PHOS-TOT
MG/L P
0.064
0.053
0.079
0.149
0.047
0.050
0.047
0.058
00300
DO
MG/L
7.2
6.8
5.4
2.0
8.8
8.4
8.2
8.2
32217
CHLRPHYL
A
UG/L
2.9
1.9
00077
TRANSP
SECCHI
INCHES
24
23
00031
INCDT LT
REMNING
PERCENT
1.0
50.0
1.0
00094
CNDUCTVY
FIELD
MICROMHO
407
406
404
402
329
329
331
331
00400
PH
SU
8.60
8.40
8.10
7.90
8.13
8.17
8.17
8.15
00410
T ALK
CAC03
MG/L
161
161
162
167
167
162
164
164
00610
NH3-N
TOTAL
MG/L
0.060
0.060
0.120
0.190
0.020
0.030
0.030
0.030
00
00625
TOT KJEL
N
MG/L
0.800
0.400
0.500
0.500
0.600
0.300
0.300
0.500
00630
N02&N03
N-TOTAL
MG/L
1.380
1.260
1.100
0.870
0.770
0.760
0.750
0.740
00671
PHOS-DIS
ORTHO
MG/L P
0.039
0.024
0.024
0.017
0.014
0.013
0.013
0.012
-------
APPENDIX E
TRIBUTARY AND WASTEWATER
TREATMENT PLANT DATA
-------
STORE! RETRIEVAL DATE 76/05/0*
DATE TIME DEPTH N02S.N03
FROM OF
TO DAY FEET
74/10/12
74/11/09
74/12/14
75/01/12
75/02/OB
75/03/09
75/04/13
75/05/11
75/05/24
75/06/07
75/06/21
75/07/13
75/07/27
75/08/10
75/09/07
13 15
14 10
13 50
11 45
13 20
08 45
11 45
12 50
15 20
14 10
13 10
13 00
14 45
13 25
13 00
2011A1
39 36 35.0 095 25 17.0 4
DELAWARE RIVER
20 . 7.5 P.ERRY
G/PERRY RESERVOIR 091191
dANK SAMPLE .5 Ml 3ELOW PERRY DAM
11EPALES 2111204
0000 FEET DEPTH CLASS 00
'0630
IS.N03
OTAL
IG/L
0.840
0.760
0.624
0.552
0.490
0.472
0.460
0.345
0.345
0.330
0.840
0.760
0.270
0.085
0.600
00625
TOT KJEL
N
MG/L
0.800
0.700
0.600
0.500
0.300
1.000
1.0?5
0.850
1.000
0.550
0.500
0.550
1.250
1.250
0.650
00610
NH3-N
TOTAL
MG/L
0.025
0.035
0.008K
0.072
C.016
0.040
0.050
0.055
0.105
0.020
0.027
0.080
0.340
0.320
0.040
00671
PriOS-DIS
ORTHO
MG/L P
0.020
0.020
0.010
0.030
0.008K
0.008K
0.005
0.005
0.015
0.005
0.025
0.030
0.020
0.040
0.030
00665
PH05-TOT
MG/L P
0.045
0.020
0.030
0.042
0.020
0.020
0.035
0.040
0.080:
0.0 40;
0.080
0.110
0.120.
0.165
0.090
K VALUE KNOrfN TO BE
LESS THAN INDICATED
-------
STORET RETRIEVAL DATE 76/05/04
DATE TIME DEPTH N02&N03
FROM OF
TO DAY FEET
74/11/09
75/01/11
75/02/08
75/03/08
75/04/12
75/05/11
75/05/24
75/06/07
75/06/21
75/07/13
75/07/27
75/08/10
75/09/07
15 05
09 35
10 55
09 40
09 55
09 40
09 30
09 55
10 ?5
10 15
08 15
07 30
09 20
09 ?5
2011A2
39 20 25.0 095 26 bO.O 4
DELAWARE RIVER
20 7.5 VALLEY FALLS
T/PEnRY RESERVOIR 091191
ST RT 16 3RDG .5 MI E OF VALLEY FALLS
11EPALES 2111204
0000 FEET DEPTH CLASS 00
0630
!i.N03
OTAL
10/L
0.400
0.341
0.480
0.400
1.000
0.300
0.125
0.095
1.200
1.450
0.005
0.010
0.005
0.300
00625
TOT KJEL
N
MG/L
1.100
1.50C
1.100
2.100
1.350
0.600
1.050
1.050
0.800
0.950
0.450
0.450
0.800
0.850
00610
NH3-N
TOTAL
MG/L
0.047
0.030
0.064
0.232
0.124
0.030
0.050
0.025
0.025
0.035
0.020
0.020
0.045
0.015
00671
PHOS-OIS
ORTHO
MG/L P
0.125
0.110
0.205
0.104
0.116
0.090
0.060
0.040
0.103
0.105
0.070
0.080
0.060
0.070
00665
PHOS-TOT
MG/L P
0.150
0.140
0.220
0.320
0.180
0.140
0.140
0.120
0.320
0.320
0.140
0.110
0.140
0.200
-------
STORE! RETRIEVAL DATE 76/05/04
2011A3
39 22 20.0 095 28 45.0 4
DELAWARE RIVER
20 7.5 VALLEY FALLS
T>PE*RY RESERVOIR
BROG ON N-S RO 1 M W
0000 FEET DEPTH
091191
2 M N VLY FALLS
2111204
CLASS 00
DATE
FROM
TO
74/10/12
74/11/09
74/ 12/14
75/01/11
75/02/08
75/03/08
75/04/12
75/05/11
75/05/24
75/06/07
75/06/21
75/07/13
75/07/27
75/08/10
75/09/07
00630 00625
TIME DEPTH N02&N03 TOT KJEL
OF N-TOTAL N
DAY FEET
10
10
10
11
10
10
10
10
10
10
10
08
08
09
10
10
00
05
20
05
30
05
00
30
50
30
50
00
50
05
MG/L
0
0
0
0
1
1
0
0
0
1
1
0
0
0
0
.168
.352
.352
.800
.800
.155
.155
.450
.540
.250
.400
.125
.090
.045
.260
MG/L
1.
0.
0.
1.
1.
1.
0.
1.
1.
1.
1.
0.
0.
0.
1.
400
800
900
500
600
350
850
500
500
450
950
300
550
550
050
00610 00671 00665
NH3-N PHOS-DIS PhOS-TOT
TOTAL ORTHO
MG/L
G.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
465
240
025
096
480
234
020
015
030
050
015
010
020
030
015
MG/L
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
p
143
160
110
130
176
144
130
115
150
150
140
110
130
055
145
MG/L P
0.360
0.190
0.140
0.160
0.270
0.280
0.230
0.480
0.380
0.400
0.720
0.160
0.230
0.220
0.380
-------
STORET RETRIEVAL DATE 76/05/04
2011^1
39 11 40.0 095 23 32.0 4
SLOUGH CREEK
20 7.5 OZA*KIE
T/PEKRY RESERVOIR 091191
dRDG 5.4 M SE OF OLD T«(N PUBLIC USE AREA
11EPALES 2111204
0000 FEET DEPTH CLASS 00
DATE
FROM
TO
74/10/12
74/11/09
74/12/14
75/01/13
75/02/08
75/03/09
75/04/13
75/05/11
75/05/24
75/06/07
75/06/21
75/07/13
75/07/27
75/08/10
75/09/07
00630 00625
TIME DEPTH N02&N03 TOT KJEL
OF N-TOTAL N
DAY FEET
12
12
13
13
12
09
11
12
14
13
12
12
11
12
12
45
50
15
50
55
20
00
25
25
40
45
20
00
55
35
MG/L
0.
0.
0.
0.
0.
0.
0.
0.
1.
0.
0.
0.
0.
0.
0.
264
750
312
920
270
528
135
460
400
400
345
200
010
005
620
MG/L
2
0
0
0
0
0
0
1
1
0
0
0
1
1
1
.000
.300
.300
.700
.700
.700
.450
.550
.450
.525
.600
.450
.050
.100
.750
00610 00671 00665
NH3-N PHOS-DIS PHOS-TOT
TOTAL ORTHO
MG/L
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
.050
.040
.030
.072
.064
.040
.015
.015
.075
.025
.010
.055
.010
.020
.165
MG/L P
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
.075
.060
.025
.104
.032
.040
.010
.035
.050
.010
.040
.005
.015
.015
.045
MG/L P
0.070
0.045
0.104
0.050
0.060
0.050
0.230
0.200
0.095
0.120
0.060
0.140
0.150
0.33C
-------
STORE! RETRIEVAL DATE 76/05/04
DATE TIME DEPTH N02&N03
FROM OF
TO DAY FEET
74/10/12
7^/11/09
74/12/14
75/01/11
75/02/08
75/04/13
75/05/11
75/05/24
75/06/07
75/06/21
75/07/13
75/07/27
75/08/10
75/09/07
12 15
11 30
12 20
13 15
12 05
10 35
11 25
12 40
13 25
12 30
11 50
10 45
12 40
12 15
20 1 i C1
39 13 20.0 095 25 15.0 4
LITTLE SLOUGH CREE*
20 7.5 pZAWtSJE
T/PErtRr RESERVOIR 091191
SEC *D BROG .8 Ml S OF ST RT 92 JCT
IIE^ALES 2111204
0000 FEET DEPTH CLASS 00
0630
&N03
OTAL
iG/L
0.336
0.760
0.288
1.240
0.720
0.110
0.230
4.000
0.330
0.375
0.135
0.085
0.005
0.440
00625
TOT KJEL
N
MG/L
3.100
0.4QO
0.300
1.600
0.800
0.750
0.700
2.900
0.800
1.100
0.550
1.450
1.800
1.550
00610
NH3-N
TOTAL
MG/L
0.470
0.035
0.015
0.048
0.024
0.030
0.020
0.340
0.015
0.005
0.030
0.150
0.020
0.123
00671
PriOS-OIS
ORTHO
MG/L P
0.100
0.035
0.010
0.035
0.016
0.007
0.015
0.070
0.005K
0.015
0.010
0.020
0.020
0.020
00665
PHOS-TOT
MG/L P
0.780
0.050
0.020
0.160
0.020
0.010
0.090
0.230
0.070
0.140
0.050
0.170
0.230
0.270
K VALUE KNOWN TO BE
LESS THAN INDICATED
-------
STORE! RETRIEVAL DATE 76/05/04
DATE TIME DEPTH N02&N03
FROM Of
TO DAY FEET
74/10/13
74/11/09
74/12/14
75/01/11
75/02/08
75/03/08
75/04/13
75/05/11
75/05/24
75/06/07
75/06/21
75/07/13
75/07/27
75/09/07
10 58
10 45
11 15
12 30
11 00
12 00
11 05
10 50
11 55
11 55
11 20
09 50
08 55
11 00
2011D1
39 21 00.0 095 25 21.0 4
BRUSi CREEK
20 7.5 VALLEY FALLS
T/PERRY RESERVOIR 0911*1
BROG 2.7 MI HE OF VALLEY FALLS
11EPALES 2111204
0000 FEET DEPTH CLASS 00
0630
'&N03
OTAL
IG/L
0.024
0.650
0.750
2.640
3.800
1.055
0.300
0.290
0.390
0.620
0.530
0.020
0.015
0.015
00625
TOT KJEL
N
MG/L
0.850
1.100
0.600
1.300
0.500
0.650
1.150
0.700
0.950
0.700
0.450
0.350
0.450
1.225
00610
NH3-N
TOTAL
MG/L
0.075
0.040
0.025
0.040
0.208
0.040
0.025
0.020
0.030
0.030
0.025
0.025
0.035
0.030
00671
PHOS-DIS
ORTHO
MG/L P
0.035
0.035
0.015
0.035
0.032
0.016
0.005K
0.010
0.015
0.015
0.045
0.010
0.025
0.025
00665
PHOS-TOT
MG/L P
0.085
0.035
0.030
0.190
0.070
0.030
0.010K
0.070
0.045
0.050
0.085
0.040
0.070
0.185
K VALUE KNOWN TO BE
LESS THAN INDICATED
-------
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
75/04/13
75/05/11
75/05/24
75/06/07
75/06/21
75/07/13
75/07/27
75/08/10
75/09/07
09 15
09 05
09 00
10 20
09 15
09 25
09 10
09 05
09 25
09 55
16 30
07 15
06 30
08 45
09 10
2011E1
39 11 30.0 095 33 05.0 4
ROCK CREEK
20 7.5 HER I DEN
T/PE«RY RESERVOIR- 091191
SEC 30 dROG 1 MI E OF MERIDEN
11EPALES 2111204
0000 FEET DEPTH CLASS 00
0630
&N03
OTAL
G/L
0.144
1.360
0.780
1.400
1.300
0.90S
0.260
0.660
0.860
1.050
1.300
0.710
0.320
1.000
0.690
00625
TOT KJEL
N
MG/L
.4.400
1.500
0.200
1.300
0.700
0.750
0.475
1.030
1.100
1.000
0.800
0.800
1.150
3.300
1.450
00610
NH3-N
TOTAL
MG/L
0.903
0.400
0.020
0.072
0.056
0.028
0.025
0.035
0.090
0.040
0.020
0.040
0.210
0.280
0.175
00671
PHOS-DIS
URTHO
MG/L P
0.025
0.025
0.005
0.035
0.016
0.008
0.010
0.020
C.025
0.030
0.035
0.005K
0.010
0.030
0.040
00665
PHOS-TOT
MG/L P
0.040
0.020
0.220
0.030
0.030
0.020
0.215
0.090
0.120
0.130
0.040
0.130
0.260
0.220
K VALUE KNOWN TO 8E
LESS THAN INDICATED
-------
STORE! RETRIEVAL DATE 76/05/04
2011E2
39 12 32.0 095 34 10.0 4
rtOCK CREEK
20 7.5 MERIDEN
T/PE?RY RESERVOIR 091191
BRDG ON LGriT OTY «G 1 MI N OF MERIDEN
11EPALES 2111204
0000 FEET DEPTH CLASS 00
DATE
FROM
TO
74/10/12
74/11/09
74/12/14
75/01/11
75/02/08
75/03/08
75/04/12
75/05/11
75/05/24
75/06/07
75/06/21
75/07/13
75/08/10
75/09/07
00630 00625
TIME DEPTH N02&N03 TOT KJEL
OF M-TOTAL N
DAY FEET
09
14
08
10
08
09
08
08
09
09
09
07
08
08
35
40
45
00
35
05
55
45
00
40
45
35
30
45
MG/L
0
0
0
2
0
0
0
0
1
0
0
0
1
1
.416
.400
.288
.800
.290
.605
.020
.500
.000
.510
.630
.980
.050
.150
MG/L
1.
0.
0.
1.
0.
0.
0.
1.
1.
0.
0.
0.
0.
1.
900
700
700
600
600
400
600
200
850
800
450
500
600
200
00610 00671 00665
NH3-N PHOS-DIS PHOS-TOT
TOTAL ORTHO
MG/L
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
055
050
015
056
040
016
020
080
123
025
015
040
055
075
MG/L
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
P
045
050
005
030
016
012
015
015
025
025
025
015
015
055
MG/L P
0.470
0.140
0.040
0.170
0.040
0.040
0.020
0.180
0.120
0.120
0.070
0.030
0.050
0.230
-------
STORE! RETRIEVAL DATE 76/05/04
DATE TIME DEPTH N02&N03
FROM OF
TO DAY FEET
74/10/12
74/11/09
74/12/14
75/01/12
75/02/08
75/03/09
75/04/13
75/05/11
75/05/24
75/06/07
75/06/21
75/07/13
75/08/10
75/09/07
13 00
13 05
13 30
12 20
13 05
09 10
11 25
12 40
14 50
13 50
12 55
12 40
13 10
12 45
2011F1
39 09 55.0 095 23 07.0 4
EVANS CREEK
20 7.5 OZAWKlt
T/PE-fRY RESERVOIR 091191
BRDG 6.5 MI S« OF OSKALOOSA
11EPALES 2111204
0000 FEET DEPTH CLASS 00
0630
'&N03
OTAL
IG/L
0.810
0.448
0.152
0.368
0.208
0.160
0.015
0.015
0.200
0.130
0.210
0.155
0.010
0.060
00625
TOT KJEL
N
MG/L
2.400
0.500
0.200
1.200
0.300
1.100
0.250
0.050K
0.800
0.350
0.400
0.400
0.200
0.350
00610
NH3-N
TOTAL
MG/L
0.030
0.030
0.017
0.032
0.056
0.024
0.020
0.010
0.025
0.025
0.015
0.025
0.025
0.035
00671
PHOS-OIS
ORTHO
MG/L P
0.185
0.030
0.015
0.032
0.008K
0.008K
0.005K
0.005K
0.010
0.005K
0.010
0.020
0.005
0.010
00665
PHOS-TOT
MG/L P
0.440
0.030
0.015
0.032
0.010K
0.010
0.020
0.010*
0.050
0.030
0.060
0.100
0.040
0.080
K VALUE KNOWN TO BE
LESS THAN INDICATED
-------
STORET RETRIEVAL DATE 76/05/04
DATE TIME DEPTH N028.N03
FROM OF
TO DAY FEET
74/10/12
7<*/ll/09
74/12/14
75/01/11
75/02/08
75/03/08
75/04/12
75/05/11
75/05/24
75/06/07
75/06/21
75/07/13
75/07/27
75/09/07
11
11
11
12
11
12
11
11
12
12
11
10
09
11
45
05
35
50
20
25
30
10
15
20
35
15
10
15
2011G1
39 16 12.0 095 23 15.0 4
FISHPOND CREEK
20 7.5 VALLEY FALLS
T/PEKRY RESERVOIR 091191
riRDG 7.2 MI N OF OSKALOOSA
11EPALES 2111204
0000 FEET DEPTH CLASS 00
0630
'J.N03
OTAL
G/L
0.352
1.000
0.750
1.560
4.300
0.830
0.315
0.560
4.730
1.050
0.660
0.230
0.025
0.590
00625
TOT KJEL
N
MG/L
3.700
0.400
0.400
2.300
0.400
0.600
1.250
0.550
1.950
0.600
0.400
0.350
0.650
1.000
00610
NH3-N
TOTAL
MG/L
0.600
0.030
0.015
0.032
0.072
0.016
0.025
0.035
0.195
0.020
0.010
0.020
0.035
0.030
00671
PHOS-OIS
ORTHO
MG/L P
0.420
0.035
0.010
0.050
0.016
0.008
0.005
0.005
0.060
0.010
0.015
0.005
0.010
0.075
00665
PHOS-TOT
MG/L P
0.670
0.035
0.020
0.440
0.030
0.020
0.050
0.030
0.210
0.040
0.040
0.040
0.090
0.230
-------
STORE! RETRIEVAL DATE 76/05/04
2011AA TF2011AA P002386
39 39 00.0 095 32 OOoO 4
NORTON
20 7.5 NORTON
T/P£RRY RES. 091192
DELAWARE RIVER
11EPALES 2141204
0000 FEET DEPTH CLASS 00
OOfclO
DATE
FROM
TO
75/02/24
75/03/31
75/04/23
75/05/14
75/06/06
75/06/26
75/07/16
75/08/06
75/08/26
75/09/17
75/10/08
75/10/31
75/12/23
00625
TIME DEPTN N02&N03 TOT KJEL
OF N-TOTAL N
DAY FEET MG/L MG/L
14
08
07
10
08
10
10
11
11
11
10
14
11
00
00
45
00
30
00
00
00
00
00
30
00
00
4.640
5.400
4.700
17.300
10.500
7.900
10.500
13.500
5.100
5.600
5.600
14.700
10.500
28.000
12.000
5.200
9.700
3.700
4.600
3.750
14.000
12.500
15.500
11.000
15.000
14.500
00610
00671
00665
50051
50053
NH3-N PHOS-DIS PHOS-TOT FLOW CONOUIT
TOTAL ORTNO RATE FLOW-MGO
MG/L MG/L P MG/L P INST MGD MONTNLY
0.230
0.110
0.240
0.160
o.iao
0.460
0.580
0.350
0.620
0.087
0.175
0.140
5.000
5.700
6.000
9.200
5.500
5»200
7.500
8.800
7.700
8.200
10.500
9.400
8.100
8.900
6.700
6.200
9.700
7.200
5.500
7.500
9.400
12.500
9.500
12.000
17.500
9.850
0
0
0
0
0
0
0
0
0
0
0
0
.598
.320
.684
.604
.720
.568
.688
.744
.745
.608
.568
.598
Oo540
Oo365
Oo605
Oo598
Oo698
0 = 5^8
Oo598
Oo6<»5
Oo686
Oo568
0»588
0»554
-------
STORE! RETRIEVAL DATE 76/05/04
20U*A TF2011WA P003369
39 26 20.0 095 43 30.0 4
HOLTON
20 7.5 HOLTON
T/PERRY RES. 091191
ELKS CREEK
11E?ALES 2141204
0000 FEET DEPTH CLASS 00
DATE
FROM
TO
75/02/10
75/03/10
75/04/10
75/05/01
75/05/22
75/06/13
75/07/03
75/07/24
75/08/15
75/09/0*
75/09/25
75/10/17
75/11/06
00630
TIME DEPTH N02&N03
OF N-TOTAL
DAY FEET
09
09
09
09
09
09
09
09
09
09
09
09
09
00
00
00
00
00
00
00
00
00
00
00
00
00
MG/L
7
4
0
1
1
8
3
0
12
4
4
11
7
.0*0
.640
.880
.300
.100
.300
.800
.250
.000
.100
.100
.500
.800
00625
TOT KJEL
N
MG/L
7.000
11.000
13.500
12.300
39.000
4.100
10.050
12.000
9.700
4.200
19.500
17.000
17.000
00610 00671
NH3-N PHOS-DIS
TOTAL ORTHO
MG/L
4.000
8.300
0.270
0.079
0.320
0.050K
O.C25K
0.260
0.550
0.650
1.570
1.720
0.210
MG/L P
9.200
9.000
8,330
6.600
1,700
7.250
11.000
16.000
11.000
13.000
13.000
13oOOO
00665
PHOS-TOT
50051 50053
FLOW CONDUIT
RATE FLOW-MOD
MG/L P INST MGD MONTHLY
9
12
12
15
2
8
12
18
12
16
13
16
.600
.500
.500
.000
.200
.500
.800
• 500
.500
.000
.000
.000
0.652
0.672
0.320
0.760
0.400
0.598
0.690
0.680
0.280
0.320
0.200
0.260
Oo660
Oo679
0.380
0.698
0.270
0.624
0.680
0.680
0.280
0.380
0.380
0.250
K VALUE KNOWN TO BE
LESS THAN INDICATED
-------
STORE! RETPIEVAL DATE 76/05/04
2011YA YF2011YA P000415
39 37 30.0 095 48 30oO 4
WETMORE
20 7.5 WETMORE
T/PERRY RESERVOIR 091191
SPRING CREEK
11EPALES 2141204
0000 FEET DEPTH CLASS 00
DATE
FROM
TO
75/02/1*
75/03/1*
75/04/14
75/05/05
75/05/27
75/06/16
75/07/07
75/07/22
75/08/12
75/09/03
75/09/24
75/10/14
75/11/04
00630
TTME DEPTH NO2&.N03
Of N-TOTAL
DAY FEET
09
08
08
08
08
07
08
09
08
09
09
09
00
30
15
00
00
30
30
00
30
00
00
00
MG/L
6.730
2.400
3.600
4.500
5.300
7.200
7.700
7.000
10.500
10.500
10.500
6.300
8.400
00625
TOT KJEL
N
MG/L
18.000
26.500
11.500
8.500
8.900
2.600
5.700
3.000
2.800
2.900
3.900
3.300
12.000
00610 00671
NH3-N PHOS-DIS
TOTAL ORTHO
MG/L
3
7
0
0
0
0
0
0
0
0
0
0
.680
.300
.280
.050
.100
.050K
.280
.140
.050
.125
.075
.240
MG/L P
2
6
0
5
5
2
5
10
12
11
13
12
.810
.000
.250
.500
.000
.700
.900
.500
.000
.500
.300
.000
00665
PHOS-TOT
50051 50053
FLOW CONDUIT
RATE FLOW-MGO
MG/L P INST MGD MONTHLY
11.000
9.300
11.000
11.300
4.800
7.700
12.000
12.500
11.500
13.500
12.000
10.500
0.029
0.035
0.027
0.030
0.035
0.019
0.014
0.019
0.027
0.029
0.027
0.029
0.041
0.027
0.029
0.043
0.019
0.014
0.019
0.019
0.019
Oo027
K VALUE KNOWN TO BE
LESS THAN INDICATED
-------
STORET RETRIEVAL DATE 76/05/04
2011ZA PD2011ZA P000359
39 40 20.0 095 24 40*0 4
EVEREST
20 7.5 EVEREST
T/PERRY RESERVOIR 091192
GRASSHOPPER CREEK
HEP ALES
2141204
0000 FEET DEPTH CLASS 00
DATE
FROM
TO
75/02/24
75/03/24
75/04/24
75/05/16
75/06/06
75/07/01
75/07/18
75/08/15
75/09/06
75/09/25
75/10/20
75/11/12
75/12/02
TIME DEPTH
OF
DAY FEET
10 00
11 30
11 00
11 00
10 30
09 30
19 00
08 45
15 30
15 30
14 00
00 00
00630
N02&N03
N-TOTAL
MG/L
0.050
0.072
0.300
0.200
0.300
0.200
0.150
0.150
0.100
0.100
0.025
0.150
0.175
00625
TOT KJEL
N
MG/L
17.000
18.000
10.500
12.000
6.000
2.500
3.900
5.000
5.300
7.200
8.000
8.600
7.100
00610
NH3-N
TOTAL
MG/L
2.450
0.348
0.310
0.140
0.035
0.120
0.440
0.290
0.210
0.050
0.050
0.038
00671
PHOS-D1S
ORTHO
MG/L P
5.000
7.800
3.400
2.000
2.020
3.200
2.000
2.300
2.400
1.300
1.630
2.100
2.200
00665
PHOS-TOT
MG/L P
10.500
9.100
4.700
2.900
2.900
3.400
a. 200
2.500
2.500
1.800
2.300
3.200
3.900
50051
FLOW
RATE
INST MGD
0.033
0.033
0.033
0.033
0.033
0.033
0.033
0.033
0.033
0.033
0.033
0.033
0.038
50053
CONDUIT
FLOW-MOD
MONTHLY
0.033
0.033
0.032
0.032
0.032
0.032
0.032
0.032
0.032
0.032
0.033
0.033
0.0003
------- |