-------
been attributed to possible cultural enrichment by upstream
sources (Prather and Prophet, 1969; Prophet, Prather, and
Edwards, 1970).
B. Rate-Limiting Nutrient:
The algal assay results indicate John Redmond Reservoir was
phosphorus limited at the time the sample was collected (10/01/75).
The reservoir data indicate phosphorus limitation at all sampling
stations and times. However, because of turbidity, primary pro-
ductivity in the reservoir is light-limited rather than nutrient-
limited.
C. Nutrient Controllability:
1. Point sources—During the sampling year, point sources
contributed 24.2% of the total phosphorus load to John Redmond
Reservoir. The wastewater treatment plant at Emporia accounted
for 20.9% of this total, and nine other facilities collectively
contributed 3.2%.
The present phosphorus loading of 9.20 g/tn 2/year is over
eight times that proposed by Vollenweider (Vollenweider and Dillon,
1974) as a eutrophic loading (see page 15); however, since primary
productivity in the reservoir is light-limited rather than nutrient-
limited, point-source phosphorus control would not be expected to
result in significant improvement in the condition of the reser-
voir.
-------
2. Non-point sources--Non-point sources contributed 75.8%
of the total phosphorus input. The Cottonwood River contributed
51.2%, the Neosho River contributed 17.3%, Badger Creek contrib-
uted 1.1%, and Eagle Creek contributed 1.0%. The ungaged minor
tributaries and immediate drainage contributed an estimated 5.0%.
The phosphorus export rates of the tributaries of this reser-
voir (page 14) were similar to the rates of the tributaries of
Council Grove Reservoir* upstream in the Neosho River drainage (60,
41, and 6 kg/km2/yr) and a tributary of Marion Reservoir** upstream
in the Cottonwood River drainage (22 kg/km2/yr).
* Working Paper No. 512
** Working Paper No. 517
-------
II. RESERVOIR AND DRAINAGE BASIN CHARACTERISTICS1"
A. Morphometry :
1. Surface area: 38.04 kilometers2.
2. Mean depth: 2.0 meters.
3. Maximum depth: 7.6 meters.
4. Volume: 76.080 x 106 m3.
5. Mean hydraulic retention time: 23 days (based on outflow).
B. Tributary and Outlet:
(See Appendix C for flow data)
1. Tributaries -
Drainage Mean flow
Name area (km2)* (m3/sec)*
Neosho River 2,007.2 9.85
Eagle Creek 142.2 0.96
Cottonwood River 4,843.3 20.65
Badger Creek 72.0 0.50
Minor tributaries &
immediate drainage - 706.1 8.43
Totals 7,770.8 40.39**
2. Outlet -
Neosho River 7,808.8*** 38.73
C. Precipitation****:
1. Year of sampling: 114.5 centimeters.
2. Mean annual: 93.5 centimeters.
f Table of metric conversions—Appendix B.
tt Stoltenberg, 1975.
* For limits of accuracy, see Working Paper No. 175, "...Survey Methods,
1973-1976".
** Sum of inlets adjusted to equal the outlet flow plus evaporation.
*** Includes area of reservoir.
**** see Working Paper No. 175.
-------
III. WATER QUALITY SUMMARY
John Redmond 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
one or more depths at two stations on the reservoir (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 last 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 ^analysis. The maximum depths sampled were 1.5 meters
at station 1 and 0.9 meters at station 2.
The sampling results are presented in full in Appendix D and are
summarized in the following table.
-------
PARAMETER
TEMP (C)
OISS OXY (MG/D
CNDCTVY (MCROMO)
PH (STAND UNITS)
TOT ALK (MG/D
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/L)
SECCHI (METERS)
A. SUMMARY OF PHYSICAL AND
1ST SAMPLING ( 4/11/74)
2 SITES
RANGE MEAN MEDIAN
11.5 - 17.3 13.4 11.5
9.2 - 9.4 9.3 9.3
262. - 375. 314. 305.
8.3 - 8.3 8.3 8.3
200. - 226. 217. 226.
0.133 - 0.720 0.339 0.163
0.063 - 0.069 0.066 0.066
1.110 - l.?10 1.163 1.170
0.080 - 0.110 0.090 0.080
0.600 - 1.800 1.067 0.300
1.190 - 1.320 1.253 1.25C
1.810 - 2.910 2.230 1.970
15.2 - 16.1 15.6 15.6
0.1 - 0.2 0.2 0.2
CHEMICAL CHARACTERISTICS FOR JOHN REDMOND RESERVOIR
STORET COOE 2005
2ND SAMPLING ( 6/23/74)
2 SITES
RANGE
23.3 - 23.5
6.8 - 7.6
411. - 422.
8.3 - 8.4
153, - 163.
0.090 - 0.152
0.087 - 0.117
1.520 - 1.620
0.050 - 0.070
0.200 - 0.500
1.580 - 1.670
1.760 - 2.120
2.6 - 2.9
0.0 - 0.3 0.2 0.2
MEAN MEDIAN
23.3 23.3
7.0
418.
8.3
159.
0.112
0.101
1.575 1.580
0.062 0.065
0.300
1.650
1.860
2.7
0.325
1.637
1.900
2.7
0.2
6.9
419.
8.3
160.
0.104
0.101
3RO SAMPLING <10/ 1/74)
2 SITES
RANGE MEAN MEDIAN
15.1 - 15.6 15.4 15.4
8.0 - 8.6 8.2 8.2
263. - 333. 304. 309.
7.7 - 6.0 7.9 7.9
156. - 158. 157. 157,,
0.108 - 0.128 0.117 0.116
0.053 - 0.057 0.055 0.055
0.680 - 0.720 0.705 0.710
0.050 - 0.080 0.065 0.065 en
0.300 - 0.900 0.575 0.550
0.750 - 0.800 0.770 0.765
1.020 - 1.580 1.280 1.260
5.8 - 1<*.2 10.0 10.0
0.2 - 0.2 0.2 0.2
-------
B. Biological characteristics:
1. Phytoplankton -
Sampl i ng
Date
04/11/74
06/23/74
10/01/74
Dominant
Genera
1. Stephanodiscus sp.
2. Centric diatoms
3. Chroomonas sp.
4. Actinastrum sp.
5. Melosira sp.
Other genera
Total
1. Melosira sp.
2. Flagellates
3. Stephanodiscus sp.
4. Cyclotella ^>.
5. Oscillatoria sp.
Other genera
Total
1. Stephanodiscus sp.
2. Chroomonas sp.
3. Gloeocystis sp.
4. Cryptomonas sp.
5. Pennate diatoms
Algal Units
per ml
1,143
842
421
241
180
542
3,369
1,180
167
139
139
83
56
Total
584
-------
8
2. Chlorophyll
C.
Sampling
Date
04/11/74
06/23/74
10/01/74
Limiting Nutrient Study:
1. Autoclaved, filtered
Station
Number
1
2
1
2
1
2
Chlorophyll a
(WJ/1)
16.1
15.2
2.6
2.9
5.8
14.2
, and nutrient spiked -
Ortho P
Spike (mg/1) Cone. (m3/ll
Control
0.050 P
0.050 P + 1.0 N
1.0 N
2. Discussion -
The control yiel
cornutum, indicates
0.010
0.060
0.060
0.010
d of the
that the
Inorganic N
Cone, (mg/1)
0.152
0.152
1.152
1.152
Maximum yield
(mg/1 -dry wt.)
12.8
18.5
26.2
12.2
assay alga, Selenastrum capri-
potential primary
productivity
of John Redmond Reservoir was high at the time the sample
was collected (10/01/75). Also, the significant increase in
yield with the addition of phosphorus alone indicates the
reservoir was phosphorus limited at that time. Note that
the addition of nitrogen alone resulted in a yield not sig-
-------
nificantly different from that of the control.
The reservoir data indicate phosphorus limitation as
well. However, because of persistent turbidity, the
reservoir is light-limited rather than nutrient-limited
(Kring, 1977).
-------
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. 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 nutrient loads
at station C-l, in kg/km2/year, and multiplying by the ZZ area in km2.
The operators of the Cottonwood Falls, Emporia, and Strong City
wastewater treatment plants provided monthly effluent samples and
corresponding flow data. The operators of the wastewater treatment
plants at Hartford, Lebo, and Olpe also provided samples; however, cor-
responding flow data were not available. Nutrient loads from these
* See Working Paper No. 175.
-------
11
plants and from the wastewater treatment plants at Americus, Council
Grove, Florence, and Marion, which were not sampled, 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
Americus**
Cottonwood Fall
Council Grove**
Emporia***
Florence**
Hartford
Lebo
Marion**
01 pe
Strong City
Pop.
Served
345
s 1,076
3,000
23,879
900
539
921
2,200
463
626
Treatment
stab
stab
stab
tr.
stab
stab
stab
stab
stab
tr.
. pond
. pond
. pond
filter
. pond
. pond
. pond
. pond
. pond
filter
Mean Flow
(m3/d)
130.6
378.5
1,135.5
21,639.9
340.7
204.0
348.6
832.7
175.2
252.0
Receiving
Water
Pester Creek
Cottonwood
River
Neosho River
Cottonwood
River
Doyle Creek
Neosho River
Lebo Creek
Cottonwood
River
Eagle Creek
Cottonwood
River
2. Industrial - Unknown
* Treatment plant questionnaires.
** Anonymous, 1971.
*** More than 25% of the total waste load is from meat packing, chrome
plating, creameries, laundries, and a soy-bean mill.
-------
12
B. Annual Total Phosphorus Loading - Average Year:
1. Inputs -
kg P/ % of
Source yr total
a. Tributaries (non-point load) -
Neosho River 60,615 17.3
Eagle Creek 3,550 1.0
Cottonwood River 179,110 51.2
Badger Creek 3,710 1.1
b. Minor tributaries & immediate
drainage (non-point load) - 17,655 5.0
c. Known municipal STP's -
Americus 390 0.1
Cottonwood Falls 715 0.2
Council Grove 3,400 1.0
Emporia 73,235 20.9
Florence 1,020 0.3
Hartford 610 0.2
Lebo 1,045 0.3
Marion 2,495 0.7
01pe 525 0.2
Strong City 1,115 0.3
d. Septic tanks - Unknown ?
e. Industrial - Unknown ?
f. Direct precipitation* - 665 0.2
Total 349,855 100.0
2. Outputs -
Reservoir outlet - Neosho River 199,875
3. Net annual P accumulation - 149,980 kg.
* See Working Paper No. 175.
-------
13
C. Annual Total Nitrogen Loading - Average Year:
1. Inputs -
kg N/ % of
Source yr total
a. Tributaries (non-point load) -
Neosho River 833,685 21.3
Eagle Creek 109,935 2.8
Cottonwood River 2,116,525 54.0
Badger Creek 46,185 1.2
b. Minor tributaries & immediate
drainage (non-point load) - 545,815 13.9
c. Known municipal STP's -
Americus 1,175 <0.1
Cottonwood Falls 1,845 <0.1
Council Grove 10,205 0.3
Emporia 195,585 5.0
Florence 3,060 0.1
Hartford 1,835 <0.1
Lebo 3,130 0.1
Marion 7,480 0.2
Olpe 1,575 <0.1
Strong City 3,135 0.1
d. Septic tanks - Unknown ?
e. Industrial - Unknown ?
f. Direct precipitation* - 41,070 1.0
Total 3,922,240 100.0
2. Outputs -
Reservoir outlet - Neosho River 2,480,455
3. Net annual N accumulation - 1,441,785 kg.
* See Working Paper No. 175.
-------
14
D. Non-point Nutrient Export by Subdrainage Area:
Tributary kg P/km2/yr kg N/km.2/.yr
Neosho River 30 415
Eagle Creek 25 773
Cottonwood River 37 437
Badger Creek 52 641
E. Mean Nutrient Concentrations in Ungaged Stream:
Mean Total P Mean Total N
Tributary Cone, (mg/1) Cone, (mg/1)
Otter Creek 0.076 1.820
-------
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 9.20 3.94 103.1 37.9
Vollenweider phosphorus loadings
(g/fli2/yr) based on mean depth and mean
hydraulic retention time of John Redmond Reservoir:
"Dangerous" (eutrophic loading) 1.08
"Permissible" (oligotrophic loading) 0.54
-------
16
V. LITERATURE REVIEWED
Anonymous, 1971. Inventory of municipal waste facilities. EPA
Publ. OWP-1, vol. 7, Wash., DC.
Kring, R. Lynn, 1977. Personal communication (primary productivity
in reservoir). KS Dept. of Health & Environment, Topeka.
Prather, Joy E., and Carl W. Prophet, 1969. Zooplankton species
diversity in John Redmond, Marion, and Council Grove reservoirs,
Kansas, summer 1968. Emporia St. Res. Studies vol. XVIII(l),
KS St. Teachers Coll., Emporia.
Prophet, Carl W., Joy E. Prather, and N. Leon Edwards, 1970. Com-
parison of summer water quality features in three Grand River
reservoirs, Kansas. Emporia St. Res. Studies vol. XVIII(4),
KS St. Teachers Coll., Emporia.
Stoltenberg, Gerald A., 1975. Personal communication (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.
-------
VI. APPENDICES
17
APPENDIX A
LAKE RANKINGS
-------
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 MILFORD 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
0.123
0.055
0.040
0.067
0.163
0.023
MEDIAN
INO'RG 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
18.833
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 CRTriO 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
-------
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
fl 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
-------
PERCENT OF LAKES WITH HIGHER VALUES (NUMBER OF LAKES WITH HIGHER VALUES)
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 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 (
50 1
71 <
36 l
0 '
93 1
: 14)
! 4)
1 12)
; 8)
: 2)
: 6)
: 9)
1 11)
1 3)
[ 1)
[ 7)
I 10)
[ 5)
( 0)
! 13)
MEDIAN
INOSG N
100 <
29 (
50 (
57 (
0 (
43 (
64 <
82 <
36 <
93 (
18 <
7 1
71 <
18 <
82 1
14)
4)
7)
8)
0)
6)
9)
11)
5)
1 13)
: 2)
! 1)
; 10)
I 2)
1 ID
500-
MEAN SEC
100 1
36 (
7 1
14 1
0 1
29 1
43 1
86 1
79 1
64 1
57 1
50 i
21 i
71
93 <
; 14)
: s>
; i)
: 2)
: o)
! 4)
[ 6)
! 12)
I 11)
I 9)
I 8)
t 7)
t 3)
( 10)
t 13)
MEAN
CHLOSA
93 (
43 (
100 <
71 (
50 <
21 (
29 <
0 1
14 <
7 1
86 1
64 1
79 1
36 <
57 1
: i3>
6)
; 14)
10)
: 7)
3)
; 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 1
14 i
25 l
: 8)
9)
: i)
ID
13)
10)
: 12)
: 0)
: 7)
! 14)
: 3)
I 5)
[ 5)
I 2)
1 3)
MEDIAN
DISS ORTHO P
89 (
29 (
100 <
50 (
7 <
64 (
71 (
79 1
14 1
21 i
43 1
36 i
57 i
0 (
89 i
12)
4)
i 14)
7)
! 1)
: 9)
: 10)
[ in
; 2)
: 3)
I 6)
t 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 FLO* INFORMATION FOR KANSAS
05/03/76
LAKE CODE 2005 JOnN REDMOND
TOTAL DRAINAGE ApEA OF LAKE(SO KM) 7808.8
SUB-DRAINAGE
TRIBUTARY' AREA(SO KM)
NORMALIZED FLOnS(CMS)
2G05A1
2005A2
2005C1
200501
2005E1
2005ZZ
7808.8
2007.2
142.2
4343.3
72.0
744.1
JAN
22.65
4.25
0.43
6.21
0.25
2.38
FE8
26.33
5.95
0.59
11.89
0.31
3.11
MAR
36.81
10.19
1.42
18.97
0.76
5.95
APR
56.63
15.01
1.53
31.15
0.76
7.93
MAY
67.96
16.42
1.67
33.93
0.88
8.76
JUN
82.12
20.10
1.50
45.31
0.74
9.34
JUL
67.96
14.72
1.50
31.15
0.79
7.93
ADO SEP
I5.o6 15.29
6.23 8.78
0.48 0.63
14.^4 19.26
0.23 0.31
3.68 4.53
OCT
33.98
7.65
0.79
15.57
0.42
4.25
NOv
18.69
5.10
0.45
10.76
0.22
2.75
DEC
19.82
3.68
0.45
7.08
0.25
2.27
MEAN
38.73
9.85
0.96
20.65
0.50
5.25
SUMMARY
TOTAL
SUM OF
DRAINAGE
AREA OF
LAKE =
SUB-DRAINAGE AREAS =
7808.8
7808.8
TOTAL FLOW IN =
TOTAL FLOW OUT =
446.23
464.11
MEAN MONTHLY FLOWS AND DAILY FLOwS(CMS)
TRIBUTARY MONTH YEAR
2005A1
MEAN FLOW DAY
FLOW DAY
FLOW DAY
FLUW
2005A2
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
11.695
78.154
38. 79<*
31.149
69.093
63.430
77.022
21.832
192.838
66.261
5.267
9.769
4.531
17.840
5.947
9.061
14.725
10.477
22.370
6.230
33.980
19.822
1.218
0.991
13
10
15
12
9
8
13
10
14
10
10
13
12
23
3
11
8
8
12
18
16
28
9
14
5.947
4.474
67.394
1.444
48.705
79.854
108.737
13.989 31
272.691 29
62.580 28
3.738
11.044
0.538
25.485
3.398
17.556
9.061
7.079
21.238
3.115 28
17.556 29
0.793
0.311
0.159
57.766
353.960
10.760
5.380
28.317
-------
TRIBUTARY FLOW INFORMATION FOR KANSAS
05/03/76
LAKE CODE 2005
REDMOND
MEAN MONTHLY FLOWS AND DAILY FLOWS(CMS)
TRIBUTARY
2005C1
2005E1
2005ZZ
MONTH
YEAR
MEAN FLOW DAY
FLOW DAY
FLO* DAY
FLOW
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
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
0.425
1.671
0.821
0.963
1.727
1.756
1.501
1.246
4.248
0.215
0.016
0.023
9.628
33.980
14.442
19.539
45.307
36.812
53.802
18.972
167.069
22.653
9.061
2.152
0.821
1.104
0.311
0.765
1.133
0.991
0.850
0.396
2.152
0.096
0.048
0.011
4.248
11.893
3.398
5.947
10.194
7.362
8.212
5.097
27.184
1.048
0.311
0.159
13
10
15
12
9
8
13
10
14
10
10
13
13
10
15
12
9
8
13
10
14
10
10
13
13
23
3
11
8
8
12
10
16
10
9
13
o.oco
0.340
0.595
0.878
0.425
0.481
0.261
0.122 31
0.269 29
0.113 28
0.001
0.000
39.644
33.980
20.954
31.149
36.812
36.812
39.644
12.743 31
65.129 29
29.733 28
4.531
5.097
2.832
0.085
0.085
1.699
0.170
0.566
0.164
0.051 28
0.096 29
0.028 12
0.005
0.037
0.368
0.113
0.003
42.475
70.792
6.796
2.632
0.311
0.023
28
0.004
-------
APPENDIX D
PHYSICAL and CHEMICAL DATA
-------
STORET RETRIEVAL DATE 76/05/03
300501
38 14 35.0 095 45 23.0 3
JOHN REDMOND RESERVOIR
20031 KANSAS
100491
DATE
FROM
TO
74/04/11
74/06/23
74/10/01
DATE
FROM
TO
74/04/11
74/06/23
74/10/01
TIME
OF
DAY
13
13
10
10
09
09
00
00
00
00
50
SO
TIME
OF
DAY
13
13
10
10
10
09
09
09
00
00
00
00
00
50
SO
50
DEPTH
FEET
0000
0005
0000
0005
0000
0005
DEPTH
FEET
0000
0005
0000
0003
0005
0000
0002
0005
00010
*ATER
TEMP
CENT
11.5
11.5
23.5
23.3
15.3
15.1
00665
PHOS-TOT
MG/L P
0.163
0.133
0.112
0.096
0.118
0.128
11EPALES 2111202
0010 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 ORTHO
MG/L INCHES MICROMHO SU MG/L MG/L MG/L MG/L MG/L P
9.
7.
6.
8.
8.
9 305 8.25
* 375 8.25
0 1 415 8.40
8 411 8.30
0 9 287 7.71
0 263 7.79
226 OoOSO 0.800 1.170 0.069
226 0.110 0.600 1.210 0.066
159 0.060 0.300 1.520 0.109
153 Oo070 0.300 1.600 0.093
157 Oo070 0.900 0.680 0.056
156 0»060 0.500 0.700 0.053
32217 00031
CHLRPHYL INCDT LT
A
OG/L
16.
2.
5.
REMNING
PERCENT
1
6
1.0
a
1.0
-------
STORE! RETRIEVAL DATE 76/05/03
DATE TIME DEPTH WATER
FROM OF
TO DAY FEET
74/04/11 13 20 0000
74/06/25 09 45 0000
09 45 0002
74/10/01 10 10 0000
10 10 0003
DATE TIME DEPTH
FROM OF
TO DAY FEET
74/04/11 13 20 0000
74/06/25 09 45 0000
09 45 0002
74/10/01 10 10 0000
10 10 0002
10 10 0003
200502
38 16 30.0 095 49 15.0 4
JOHN REDMOND RESERVOIR
20031 KANSAS
100492
11EPALES 2111202
0003 FEET DEPTH CLASS 00
0010
TER
EMP
ENT
17.3
23.3
23.3
15.6
15.6
0665
iS-TOT
i/L P
0.720
0.152
0.090
0.108
00300
DO
MG/L
9.2
7.6
6.8
8.6
8.4
32217
CHLRPHYL
A
UG/L
15.2
2.9
14.2
00077
TRANSP
SECCHI
INCHES
4
12
9
00031
INCDT LT
REMNING
PERCENT
1.0
1.0
00094
CNDUCTVY
FIELD
MICROMHO
262
422
422
333
331
00400
PH
SU
8.25
8.40
8.30
8.01
8.01
00410
T ALK
CAC03
MG/L
200
163
160
158
156
00610
NH3-N
TOTAL
MG/L
0.080
0.050
0.070
0.080
0.050
00625
TOT KJEL
N
MG/L
1.800
0.500
0.200
0.600
0.300
00630
N02«»N03
N-TOTAL
MG/L
1.110
1.620
1.560
0.720
0.720
00671
PHOS-OIS
ORTHO
MG/L P
0.063
0.117
0.087
0.057
0.055
0.115
-------
APPENDIX E
TRIBUTARY AND WASTEWATER
TREATMENT PLANT DATA
-------
STORE! RETRIEVAL DATE 76/05/04
DATE TIMF DEPTH N02&N03
FROM OF
TO DAY FEET
74/10/12
74/11/10
74/12/15
75/02/09
75/03/08
75/04/13
75/05/10
75/05/31
75/06/14
75/06/29
75/07/10
75/07/28
75/08/10
75/09/13
08 40
13 ?5
09 35
10 19
15 04
08 49
14 43
16 10
15 02
14 10
20 10
16 40
12 55
12 55
2005A1
38 13 00.0 095 44 00.0 4
20 coFFer co HWY MP
O/JOMN REDMOND RESERVOIR 100491
BftuG ON US RT 75 1 HI N OF BURLINGTON
11EPALES 2111204
0000 FEET DEPTH CLASS 00
0630 00625
'&N03 TOT KJEL
OTAL N
00610 00671 00665
NH3-N PHOS-DIS PHOS-TOT
TOTAL ORTHO
IG/L MG/L MG/L
0
0
0
0
0
0
0
0
0
0
0
0
0
0
.704 ]
.600 1
.720 ]
.640 ]
.875 1
.620 ]
1.500
1.000
1.900
1.800
1.800
1.550
.230 0.900
.315 2.080
.810 ]
.670 ]
1.250
1.000
.670 0.650
.610 0.700
.290 1
.610 ]
1.850
1.900
0.
0.
0.
0.
0,
0.
0.
0,
0,
0.
0,
0,
0.
0.
,060
.125
,195
,120
.200
,084
,030
.125
,110
.032
,030
,025
.025
,065
MG/L
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
p
055
060
080
024
060
100
020
040
070
100
065
040
025
040
MG/L
0
0
0
0
0
0
0
0
0
0
0
0
0
0
•
•
•
•
•
•
•
•
•
•
•
*
•
•
p
120
130
440
160
220
140
090
110
200
180
150
120
030
110
-------
STORE! RETRIEVAL DATE 76/05/04
2005A2
38 25 00.0 096 07 15.0 4
NEOSMO RIVER
20 LYON CO H*Y MAP
T/JOHN REDMOND RESERVOIR 100492
BROG ON US RT 50 2 MI £ OF EMPORIA
11EPALES 2111204
0000 FEET DEPTH CLASS 00
DATE
FROM
TO
74/10/12
74/11/23
74/12/03
75/01/11
75/02/08
75/03/08
75/04/12
75/05/18
75/05/28
75/06/16
75/06/29
75/07/12
75/07/28
75/08/09
75/09/14
00630 00625
TIME DEPTH N02&N03 TOT KJEL
OF N-TOTAL N
DAY FEET
11
12
16
14
13
11
14
14
14
12
10
13
16
11
11
10
00
10
30
45
45
00
45
15
30
05
45
20
30
40
MG/L
0
0
0
0
0
0
0
0
1
1
0
0
0
0
0
.056
.600
.736
.830
.850
.835
.440
.330
.250
.000
.900
.732
.065
.045
.200
MG/L
2.
1.
1.
3.
1.
2.
2.
4.
2.
1.
0.
3.
2.
1.
0.
500
100
300
300
400
300
200
600
200
550
950
000
600
075
800
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.
230
045
025
432
048
080
035
085
105
015
035
195
020
110
025
MG/L
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
P
035
060
065
065
048
060
065
035
085
070
075
055
035
020
065
MG/L P
0.140
0.130
0.100
0.380
0.200
0.420
0.170
0.120
0.320
0.270
0.260
0.200
0.200
0.155
0.190
-------
STORET RETRIEVAL DATE 76/os/04
2C0581
38 11 30.0 095 51 55.0 4
OTTES CREEK
20 7.5 J REDMOND DM
T/jOiN gEOMOf^p RESERVOIR 100491
oRDG ON LGnT OTY RO b M N OF BURLINGTON
11EPALES 2111204
0000 FEET DEPTH CLASS 00
DATE
FROM
TO
74/10/13
74/11/10
74/12/15
75/01/12
75/03/08
75/04/13
75/05/10
75/05/31
75/06/14
75/06/29
75/07/10
75/07/28
75/08/10
75/09/13
00630 00625
TIME DEPTH N02&.N03 TOT KJEL
OF N-TOTAL N
DAY FEET
09
14
10
13
15
09
15
16
15
14
20
18
13
13
05
00
14
48
20
09
01
30
21
30
30
01
12
15
MG/L
0
0
0
0
0
0
0
1
0
0
0
0
0
0
.040
.690
.660
.940
.384
.185
.100
.720
.640
.220
.190
.115
.075
.970
MG/L
1.
1.
0.
3.
0.
1.
1.
1.
1.
0.
1.
0.
1.
1.
800
300
900
800
800
000
250
400
400
450
000
700
450
300
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.
0.
065
080
050
528
024
025
030
065
045
020
035
040
040
063
MG/L
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
P MG/L P
025
030
015
016
008K
015
005
035
030
010
015
015
020
035
0.070
0.060
0.050
0.060
0.020
0.020
0.020
0.130
0.120
0.030
0.030
0.030
0.130
0.200
K VALUE KNOWN TO BE
LESS THAN INDICATED
-------
STORE! RETRIEVAL DATE 76/05/04
2005C1
38 16 00.0 096 10 30.0 4
EAGLt CREEK
20 LtON CO HWY MAP
T/jOnN rtEOMONO RESERVOIR 100492
o«OG ON GRAVEL RD 8 MI E OF" OLPE
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
75/03/08
75/04/13
75/05/10
75/05/31
75/06/14
75/06/29
75/07/28
75/08/10
75/09/13
00630 00625
TIMF DEPTH N02S.N03 TOT KJEL
OF N-TOTAL N
DAY FEET MG/L MG/L
09
14
10
15
11
15
09
15
16
13
15
18
13
13
25
55
48
08
01
43
32
26
50
45
10
20
35
35
0
0
1
1
1
0
0
0
2
1
0
0
0
0
.016 2.500
.980
.160
.920 «
.650
.825
.375
.000
.400
j.OOO
.200
.100
.650
.240 0.950
.600 2.000
.650 1.800
.520 4.400
.050 0.650
.015 1.100
.005 1.200
00610 00671 00665
NH3-N PHOS-DIS PHOS-TOT
TOTAL ORTHO
MG/L MG/L P MG/L P
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
040
065
050
280
128
048
025
030
075
065
085
020
020
020
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
085
070
060
080
056
028
020
025
065
055
025
025
030
025
0
0
0
0
0
0
0
0
0
0
0
0
0
0
.150
.150
.170
.320
.170
.090
.100
.100
.250
.210
.090
.080
.150
.135
-------
STORET RETRIEVAL DATE 76/05/04
DATE TIME DEPTH N02&N03
FROM OF
TO DAY FEET
74/10/13
74/11/10
74/12/15
75/01/12
75/02/09
75/03/08
75/04/13
75/05/10
75/05/31
75/06/14
75/06/29
75/07/10
75/07/28
75/08/10
75/09/13
09 50
15 30
11 19
14 31
11 ?4
16 01
09 54
15 45
17 15
16 08
15 30
21 20
18 45
14 05
14 05
2005D1
38 22 00.0 096 07 00.0 4
COTTONWOOD RIVER
20 LYON CO HWY .MAP
T/jOri,M REDMOND RESERVOIR 100491
6RDO> ON GRAVEL RD 2.8 MI S JCT US RT 50
11EPALES 2111204
0000 FEET DEPTH CLASS 00
0630
I&N03
OTAL
IG/L
0.368
0.840
0.552
0.464
0.930
0.875
0.860
0.780
1.950
1.200
1.300
0.980
0.075
0.300
1.720
00625
TOT KJEL
N
MG/L
5.500
1.900
1.900
5.000
2.200
2.200
2.050
1.500
3.200
2.300
1.850
1.350
1.950
3.750
3.800
00610
NH3-N
TOTAL
MG/L
1.720
0.670
0.730
0.910
0.588
0.384
0.230
0.400
0.095
0.110
C.145
0.250
0.550
0.360
1.100
00671
PHOS-OIS
ORTHO
MG/L P
0.175
0.125
0.070
0.080
0.112
0.140
0.174
0.125
0.100
0.115
0.135
0.120
0.190
0.300
0.210
00665
PHOS-TOT
MG/L P
0.770
0.250
0.140
0.190
0.310
0.200
0.380
0.240
0.730
0.580
0.520
0.290
0.320
0.480
0.540
-------
STORE! RETRIEVAL DATE 76/05/04
2005E1
38 24 30.0 096 03 30.0 4
BADGES CREEK
20 LrON CO H*Y MAP
T/jOHN REDMOND RESERVOIR 100492
0ROG ON US RT 50 6 MI E OF EMPORIA
11EPALES 2111204
0000 FEET DEPTH CLASS 00
DATE
FROM
TO
74/10/13
74/11/23
74/12/03
75/01/11
75/02/08
75/03/08
75/04/12
75/05/10
75/05/28
75/06/16
75/06/29
75/07/10
75/07/12
75/07/28
75/08/09
75/09/13
00630 00625
TIME DEPTH N02S.N03 TOT KJEL
OF N-TOTAL N
DAY FEET
11
11
16
14
11
13
15
13
12
13
20
14
16
11
14
25
45
25
40
25
30
00
45
45
00
52
25
00
15
20
MG/L
0
0
0
1
1
0
0
0
1
0
1
0
0
0
0
0
.040
.320
.160
.010
.060
.774
.350
.095
.880
.590
.000
.005
.035
.030
.010
.280
MG/L
1.
0.
1.
3.
1.
2.
1.
3.
2.
3.
2.
0.
2.
0.
2.
0.
500
900
500
400
300
700
350
700
600
150
000
950
300
875
000
500
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.
0.
030
030
020
304
112
088
030
085
110
046
115
065
040
040
155
085
MG/L
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
P
035
030
015
105
040
060
015
020
085
030
050
020
010
022
CIO
005
MG/L P
0.190
0.130
0.060
0.420
0.140
0.420
0.100
0.100
0.390
0.220
0.245
0.140
0.090
0.120
0.130
0.040
-------
STO*ET RETRIEVAL OATt 76/05/04
2005CA P02005CA P000463
38 15 50.0 096 10 00.0 4
OLPE
20 LYON COUNTY
T/JOHN REDMOND RES. 10 !"-92
EAGLE CREEK
IIE^ALES 21412C-
0000 FEET DEPTH CLASS 00
DATE
FROM
TO
75/02/10
75/03/13
75/04/08
75/04/28
75/05/19
75/06/09
75/07/01
75/07/21
75/08/11
75/09/02
75/09/22
75/10/14
75/11/03
TIME
OF
DAY
12 30
12 30
12 30
12 30
12 30
12 30
12 30
12 30
12 30
12 30
12 30
12 30
12 30
FEET
00630
N02&N03
N-TOTAL
MG/L
0.080.
0.480
0.315
0.050
0.700
0.150
0.150
0.025
0.029
0.125
0.400
0.075
0.325
00625
TOT KJEL
N
MG/L
24.000
4.600
17.000
17.500
8.200
5.600
8.600
8.700
17.500
11.500
15.300
25.000
32.000
00610
NH3-N
TOTAL
MG/L
7.91C
2.500
5.700
0.210
0.210
0.130
0.700
0.690
0.710
3.700
5.700
00671
PHOS-DIS
ORTHO
MG/L P
5.900
3.700
6.200
2.300
3.200
4.700
3.600
6.600
5.200
6.350
9.600
00665
PHOS-TOT
MG/L P
6.600
3.900
5.600
6.700
2.800
4.300
5.100
5.000
8.500
6.100
11.000
11.000
12.900
50051 50053
FLO* CONDUIT
RATE FLOw-MGO
INST M'30 MONTHLY
-------
STORE! RETRIEVAL DATE 7-i/03/04
DATE
FROM
TO
75/02/12
75/03/13
75/04/17
75/05/12
75/06/04
75/06/30
75/07/22
75/08/05
75/09/10
75/09/24
75/10/06
75/11/03
75/12/10
TIME DEPTH
OF
DAY FEET
03 00
08 30
10 30
10 00
00
00
11 00
09 00
16 00
08 00
09 30
10 00
11
11
20050A P02005DA P001076
38 22 00.0 096 31 30.0 4
COTTOiNaOOO FALLS
20 CHASE COUNTY
T/JOHN REDMOND RES. 100491
COTTON*OOD RIVER
11EPALES 2141204
oooo FEET DEPTH CLASS oo
10 00
ilOC
1 -, -<0 3
". ~ - •_
'•'-• / L
C.320
C . 0 = i
0.--OG
C.05C
0.050
C.200
0 .025
0.028
0.075
0.050
0.150
0.025
0. 150
00625
TOT KJEL
N
MG/L
3.500
14.500
18.500
16.000
6.100
15.700
16.000
16.500
25.000
22.000
18.000
17.000
00610
NH3-N
TOTAL
MG/L
0.170
0.660
0.160
0.050K
0.050K
0.100
0.050K
0.025K
0.025K
0.025K
0.100K
0.125
0.400
00671
PHOS-DIS
ORTHO
MG/L P
6.200
1.400
1.700
2.000
2.600
1.150
1.330
1.500
1.800
1.700
2.700
6.200
00665
PHOS-TOT
MG/L P
6.100
7.200
4.500
3.700
4.400
3.200
1.200
2.600
3.000
4.200
4.100
4.100
11.000
50051
FLOW
RATE
INST MOD
0.100
0.100
0.100
0.100
50053
CONDUIT
FLOrt-MGD
MONTHLY
0.100
0.100
0.100
0.100
K VALUE KNOWN TO BE
LESS THAN INDICATED
-------
STORE! RETRIEVAL DATE 76/05/04
DATE TIME DEPTH N02&N03
FROM OF
TO OAY FEET
75/04/30
75/06/04
75/06/30
75/08/01
75/09/30
75/10/30
76/01/02
76/03/26
76/03/29
08 30
08 00
07 40
13 00
10 30
08 00
08 00
09 30
08 00
200506 TF200SOB P000626
38 23 30.0 096 33 00.0 4
STRONG CITY
20 7.5 STRONG CITY
T/JOriN REDMOND RES. 100491
COTTONnOOO RIVER
11EPALES 2141204
0000 FEET DEPTH CLASS 00
0630
'&N03
OTAL
IG/L
0.050
0.500
1.100
2.200
2.880
0.100
0.040
00625
TOT KJEL
N
MG/L
20.000
31.000
5.900
46.000
27.000
41.000
38.000
00610
NH3-N
TOTAL
MG/L
2.700
4.650
0.087
18.000
9.700
26.000
25.000
00671
PHOS-DIS
ORTMO
MG/L P
5.350
2.880
1.650
5.900
12.000
5.100
00665
PHOS-TOT
MG/L P
6.450
8.300
3.800
13.000
13.000
16.300
14.000
50051
FLOW
RATE
INST MOD
0.031
0.072
0.080
0.080
0.060
0.060
0.550
0.060
0.054
50053
CONDUIT
FLO«-MGO
MONTHLY
0.081
0.070
0.080
0.070
0.060
0.060
0.045
0.060
0.054
-------
STORE! RETRIEVAL DATE 76/05/0*
00630 00625
DATE TIME DEPTH N02&N03 TOT KJEL
FROM OF N-TOTAL N
TO DAY FEET MG/L MG/L
75/03/02 12 00
CP(T)-
75/03/03 12 00
75/04/02 12 00
CP(T)-
75/04/02 12 00
75/05/16 01 00
CP(T>-
75/05/16 24 00
75/05/20 24 00
CP(T)-
75/05/21 24 00
75/06/06 24 00
CP(T>-
75/06/07 24 00
75/07/08 12 00
CP(T)-
75/07/09 12 00
75/07/25 24 00
CPIT)-
75/07/26 24 00
75/08/10 24 00
CP(T)-
75/08/11 24 00
75/09/10 12 00
CP(T>-
75/09/11 12 00
75/10/02 12 00
CP(T)-
75/10/03 12 00
75/10/21 24 00
75/11/23 12 00
CP(T)-
75/11/23 24 00
2005DC TF2005DC P023879*
38 23 00.0 096 10 00.0 4
20 7.5 EMPORIA
T/joi-iN REDMOND RES. 100*91
COTTONWOOD RIVER
11EPALES 2141204
0000 FEET DEPTH CLASS 00
00610 00671 00665 50051 50053
NH3-N PHOS-DIS PHOS-TOT FLOW CONDUIT
TOTAL ORTHO RATE FLOW-MGO
MG/L MG/L P MG/L P INST MGD MONTHLY
0.080
0.345
0.200
0.100
1.000
0.300
2.300
3.100
0.025
0.425
O.OSC
3.600
26.000
42.000
27.000
21.000
23.000
25.000
14.500
13.000
23.000
22.000
16.000
24.000
10.800
20.090
14.500
14.500
10.500
6.000
9.800
2.800
10.500
7.900
8.000
14.500
7.600
3.130
7.400
7.020
7.300
7.700
7.900
9.100
7.900
8.500
9.400
7.900
10.500
13.000
7.700
7.300
8.600
8.800
8.800
9.300
8.500
9.600
9.600
8.600
4.300
8.800
7.600
6.500
8.300
6.500
5.000
4.600
6.600
5.900
6.300
2.400
4.800
4.800
7.100
7.000
8.100
6.300
5.500
5.600
6.000
5.200
5.600
2.600
-------
STORET RETRIEVAL DATE 76/05/04
2005XA P02005XA P000921
38 24 30.0 095 52 00.0 4
LEBO
20 7.5 LEBO
f/JOriN REDMOND RES 091492
LEriO WEEK
11EPALES 2141204
0000 FEET DEPTH CLASS 00
DATE TIME DEPTH
FROM OF
TO DAY FEET
75/02/25 16 00
75/03/18 14 00
75/04/29 10 00
75/05/19 10 00
75/06/10 10 30
75/07/02
75/07/22
75/08/11 11 00
75/09/03
75/09/25
75/10/24 09 00
75/11/12 00 00
75/12/02 00 00
00630
N02&N03
N-TOTAL
MG/L
0.300
0.400
0.450
0.050
0.100
0.050
0.100
0.075
0.050
0.050
0.050
0.825
1.100
00625
TOT KJEL
N
MG/L
17.500
3.700
14.000
9.000
10.000
9.400
10.500
11.000
12.000
14.000
13.000
12.000
11.000
00610
NH3-N
TOTAL
MG/L
1.950
1.360
0.770
0.057
0.050K
0.069
0.050K
0.025K
0.025K
0.025K
0.080
0.044
0.100
00671
PHOS-DIS
ORTHO
MG/L P
10.500
9.300
4.000
2.300
4.000
1.850
1.500
2.300
2.000
2.800
4.300
6.000
6.575
00665
PHOS-TOT
MG/L P
12.000
10.000
4.700
3.000
5.900
3.000
2.500
3.400
3.200
4.200
5.000
7.200
9.600
50051
FLO*
RATE
INST MGD
0.001
0.768
50053
CONDUIT
FLOrt-MGD
MONTHLY
K VALUE KNOWN TO BE
LESS THAN INDICATED
-------
5TORET RETRIEVAL DATE 76/05/04
200521 P0200521 P000539
38 18 00.0 095 57 15.0 4
HARTFORD
20 LYON COUNTY
D/JOHN REDMOND RES 100491
JOHN REDMOND RES
11EPALES 2141204
0000 FEET DEPTH CLASS 00
DATE
FROM
TO
75/01/07
75/02/07
75/03/06
75/04/05
75/05/06
75/06/03
75/07/07
75/08/07
75/09/02
75/10/06
75/11/02
75/12/01
76/01/06
00630
TIME DEPTH N02&N03
OF N-TOTAL
DAY FEET
14
10
09
10
10
13
10
15
12
10
14
09
00
30
30
00
00
00
00
30
00
00
00
00
MG/L
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
480
080
080
551
050
150
100
050
025
100
100
275
350
00425
TOT «JEL
N
MG/
27.
23.
24.
19.
18.
8.
22.
19.
16.
21.
20.
11.
16.
00610 00671 00665 50051 50053
NH3-N PHOS-DIS PHOS-TOT FLOW CONDUIT
TOTAL ORTHO RATE FLOw-MGD
MG/L
500
300
500
000
500
300
;00
500
500
700
)00
000
•>00
8
8
5
0
2
0
0
0
1
0
0
0
0
.200
.900
.400
.227
.200
.081
.250
.310
.700
.280
.100
.160
.110
MG/L
2.
5.
3.
4.
2.
3.
1.
4.
6.
2.
2.
3.
2.
P
700
700
100
160
400
400
200
600
100
800
800
050
700
MG/L P INST MGD MONTHLY
5.500
8.350
8.600
6.000
9.000
6.800
6.900
7.300
8.200
9.000
9.800
4.800
5.500 0.594 0.544
-------