U.S. ENVIRONMENTAL PROTECTION AGENCY
NATIONAL EUTROPHICATION SURVEY
WORKING PAPER SERIES
REPORT
ON
RESERVOIR
CONVERSE AND PLATTE COUNTIES
WYOMING
EPA REGION VI11
WORKING PAPER No, 887
CORVALLIS ENVIRONMENTAL RESEARCH LABORATORY - CORVALLIS, OREGON
and
ENVIRONMENTAL MONITORING & SUPPORT LABORATORY - LAS VEGAS, NEVADA
-------
REPORT
ON
GLJENDO
CONVERSE AND PLATE COUNTIES
MING
EPA REGION VIII
WORKING PAPER No, 887
WITH THE COOPERATION OF THE
WYOMING DEPARTMENT OF ENVIRONMENTAL QUALITY
AND THE
WYOMING NATIONAL GUARD
JUNE, 1978
-------
CONTENTS
Page
Forward ii
List of Wyoming Lakes and Reservoirs iv
Lake and Drainage Area Map v>vi
Sections
I. Conclusions
II. Reservoir and Drainage Basin Characteristics
III. Water Quality Summary
IV. Nutrient Loadings
V. Literature Reviewed
VI. Appendices
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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.
-------
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 Wyoming Department of Environ-
:mental Quality for professional involvement, to the Wyoming National
Guard for conducting the tributary sampling phase of the Survey,
and to those Wyoming wastewater treatment plant operators who
voluntarily provided effluent samples.
The staff of the Water Quality Division provided invaluable
lake documentation and counsel during the Survey, reviewed the
preliminary reports, and provided critiques most useful in the
preparation of this Working Paper series.
Brigadier General James L. Spence, The Adjutant General of
Wyoming, and Project Officer Colonel Donald L. Boyer, who directed
the volunteer efforts of the Wyoming National Guardsmen, are also
gratefully acknowledged for their assistance to the Survey.
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NAME
Big Sandy
Boulder
Boysen
De Smet
Flaming Gorge
Fremont
Glendo
Keyhole
Ocean
Seminoe
Soda
Viva Naughton
Woodruff Narrows
Yellowtail
IV
NATIONAL EUTRO.PHICATION SURVEY
STUDY RESERVOIRS
State of Wyoming
COUNTY
Sublette, Sweetwater
Sublette
Fremont
Johnson
Sweetwater, WY; Daggett, UT
Sublette
Converse, Platte
Crook
Fremont
Carbon
Sublette
Lincoln
Uinta
Bighorn, WY; Bighorn,
Carbon, MT
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42 45'-
lost Springs £/
\ Map Location
GLENDO RESERVOIR
Tributary Sampling Site
X Lake Sampling Site
Sewage Treatment Facility
RESERVOIR \-J
42'30'-
V
North Plane River
104*45'
-------
GLENDO RESERVOIR
^ Tributary Sampling Site
^ Sewage Treatment Facility
10 20 30 40 Km.
20 Mi.
Scale
105'30'
I
105 00'
-------
GLENDO RESERVOIR
STORE! NO. 5607
T)
I. CONCLUSIONS
A. Trophic Condition:
Survey data indicate that Glendo Reservoir is eutrophic. It
ranked twelfth in overall trophic quality when the 14 Wyoming
lakes and reservoirs sampled in 1975 were compared using a com-
bination of six parameters*. Nine of the waterbodies had less
median total phosphorus, 12 had less median inorganic nitrogen,
seven had less and two the same median dissolved orthophosphorus,
ten had less mean chlorophyll a_, and nine had greater mean Secchi
disc transparency. Marked depression of dissolved oxygen with
depth occurred at station 1 in August.
Survey limnologists observed emergent aquatic plants along
much of the shoreline in May.
B. Rate-Limiting Nutrient:
The results of the algal assays indicate that Glendo Reservoir
was phosphorus limited at the times the samples were taken (05/22/75
and 10/14/75).
The reservoir data indicate phosphorus limitation all three
sampling times.
C. Nutrient Controllability:
1. Point Sources—Known point sources contributed 1.5% of
the total phosphorus load to the reservoir during the sampling
* See Appendix A.
-------
year. The town of Glendo contributed 0.1% of the total, and
Douglas added 1.4%. Septic tanks serving near-shore dwellings
were estimated to have contributed Jess than 0.1% of the total,
but a shoreline survey is needed to determine the actual signi-
ficance of those sources.
The present phosphorus loading of 3.24 g/m2/yr is more than
three times that proposed by Vollenweider (Vollenweider and
Dillon, 1974) as a eutrophic loading (see page 12). Because of
this, all phosphorus inputs to Glendo Reservoir should be mini-
mized to the greatest possible extent to slow the aging of the
reservoir.
2. Non-point sources—Non-point sources, including precipi-
tation, accounted for 98.5% of the total phosphorus load to the
reservoir during the sampling year. The North Platte River con-
tributed 97.8% of the total, and the minor tributaries and im-
mediate drainage added less than 0.1%.
The non-point phosphorus export rate of the North Platte River
was 4 kg/km2/yr (see page 11). Unsampled point sources may have
contributed to this export. The cities of Casper (population = 39,000)
and Glenrock (population = 1,600) discharge to the North Platte River
100 to 130 km upstream from Glendo Reservoir and may be contributing
a significant nutrient load.
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II. RESERVOIR AND DRAINAGE BASIN CHARACTER1STICSt
A. Morphometry"t"'":
1. Surface area: 53.97 kilometers2.
2. Mean depth: 18.3 meters.
3. Maximum depth: 64.6 meters.
4. Volume: 987.651 x 106 m3.
5. Mean hydraulic retention time: 264 days (based on outflow).
B. Tributary and Outlet:
(See Appendix C for flow data)
1. Tributaries -
Drainage Mean flow
Name area (km2)* (in3/sec)*_
North Platte River 48,813.7 47.060
Whiskey Gulch 25.9 0.007
Elkhorn Creek 150.2 0.007
Cottonwood Creek 64.7 0.006
Minor tributaries &
immediate drainage - 1,414.6 Q.033
Totals 50,469.1 47.113
2. Outlet -
North Platte River 50,523.1** 43.340**
C. Precipitation***:
1. Year of sampling: 23.34 centimeters.
2. Mean annual: 31.70 centimeters
t Table of metric conversions—Appendix B
tt Prior, 1974.
* For limits of accuracy, see Working Paper No. 175, "...Survey Methods,
1973-1976".
** Includes area of reservoir; lesser outflow due to evaporation.
*** See Working Paper No. 175.
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III. WATER QUALITY SUMMARY
Glendo 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 stations 1 and 2 (because of reservoir drawdown, five other
stations were sampled only once; see map, page v). During each visit, a
single depth-integrated (4.6 m or near bottom to surface) sample was com-
posited from the stations for phytoplankton identification and enumeration;
and during the first and last visits, 18.9-liter depth-integrated samples
were composited for algal assays. Also each time, a depth-integrated
sample was collected from each of the stations for chlorophyll a^ analy-
sis. The maximum depths sampled were 20.1 meters at station 1, 21.9
meters at station 2, 7.9 meters at station 39 6.7 meters at station 4,
3.7 meters at station 53 and near-surface only at stations 6 and 7.
The sampling results are presented in full in Appendix D and are
summarized in the following table.
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PARAMETER
TEMP (C)
OISS OXY (MG/D
CNDCTVY (MCKOMO)
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)
CHLR°YL A (Uf,/L>
SECCHl (METEPS)
A. SUMMARY OF PHYSICAL AND
1ST SAMPLING ( 5/32/75)
5 SITES
RANGE
7.2 - 12.5
8.2 - 10.0
310. - 564.
8.3 - 8.7
101. - 156.
C.024 - 0.2^8
0.002 - 0.034
O.lbO - 0.370
0.0^0 - 0.090
0.31) - O.BOO
U.20C - 0.420
0.560 - 1.080
?.8 - 7.2
0.3 - 3.7
CrlEMICAL CHARACTERISTICS FOR GLtNuG RESERVOIR
STORET CODE 5to07
2ND SAMPLING ( H/27/75)
3 SITES
3RO SAMPLING (10/14/75)
3 SITES
MEAN
10. C
9.3
473.
8.5
139.
0.065
0.013
0.271
0.056
0.480
0.327
0.751
4.8
l.P
MEDIAN
10.1
9.5
521.
8.6
148.
0.041
0.007
0.280
0.050
O.bOU
0.35U
0.755
4.6
1.6
RANGE
17.8
2.4
480.
8.0
142.
0.034
0.010
0.060
0.020
0.200
0.080
0.340
3.7
0.1
- 21.0
9.0
- 567.
8.7
- 156.
- U.092
- 0.053
- 1.000
- 0.340
- 0.900
- 1.030
- U300
- 26.3
0.4
ME AIM
19.4
5.9
543.
3.3
145.
0.055
0.021
0.244
0.090
0.550
0.334
0.794
13.5
0.3
MEDIAN
19.5
6.1
554.
8.3
144.
0.054
0.017
0. 170
0.050
0.550
0.265
0. 755
10.5
0.4
RANGE
10.1
6.6
486.
8.0
151.
0.038
0.007
0.050
0.030
0.400
O.O'iO
0.430
5.b
0.3
- 12.5
8.0
- 533.
8.4
- 155.
- 0.053
- 0.019
- 0.150
- 0.140
- 0.500
- 0.290
- 0.640
- 14.3
O.b
MEAN
12.0
7.4
511.
. 4.3
152.
0.043
0.015
0.115
0.104
0.437
0.219
0.552
9.6
0.5
MEDIAN
12.2
7.5
511.
8.3
152.
0.043
0.016
0.120
0.110
0.400
0.230
0.545
a. 9
0.5
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B. Biological Characteristics:
1. Phytoplankton -
Sampling
Date
05/22/75
08/27/75
10/14/75
2. Chlorophyll a_ -
Sampling
Date
05/22/75
Dominant
Genera
1.
2.
3.
4.
5.
1.
2.
3.
4.
5.
1.
2.
3.
4.
5.
Diatoma sp.
Stephanodiscus sp_.
Cryptomonas sp.
Asterionella sp.
Navicula sp.
Other genera
Total
Aphanizomenon sp.
Navicula sp.
Diatoma sp.
Rhoicosphenia sp.
Scenedesmus sp.
Total
Navicula sp.
Melosira sp.
Diatoma sp.
Chroomonas (?) sp.
Stephanodiscus sp_.
Other genera
Algal Units
per ml
Total
Station
Number
1
2
3
4
5
6
7
2.8
3.6
7.2
5.8
4.6
1758
2407
193
48
48
48
2744
440
439
275
275
165
163
1757
Chlorophyll a_
-------
Sampling
Date
08/27/75
10/14/75
Station
Number
1
2
3
4
5
6
7
1
2
3
4
5
6
7
Chlorophyll a
(yg/1)
3.7
26.3
-
-
-
10.5
-
5.5
8.9
-
-
-
-
14.3
C. Limiting Nutrient Study:
1. Autoclaved, filtered, and nutrient spiked -
a. May sample
1). Stations 1, 2, and 3 -
Ortho P
Cone, (mg/1)
Spike (mg/1)
Control
0.050 P
0.050 P + 1.0
1.0 N
2). Stations 4 and 5 -
Spike (mg/1)
Control
0.050 P
0,050 P * 1.0 N
1.0 N
Ortho P
Cone, (mg/1)
0.025
0.075
0,075
0,025
Inorganic N
Cone, (mg/1)
Maximum yield
(mg/1-dry wt.)
0.005
0.055
0.055
0.005
0.310
0.310
1.310
1.310
1.1
14.1
17.3
1.1
Inorganic N
Cone (mg/1)
0.430
0.430
1.430
1.430
Maximum yield
(mg/1-dry wt.)
5.3
17.8
30.5
4.4
-------
0.005
0.055
0.055
0.005
0.175
0.175
1.175
1.175
0.6
13.4
19.5
0.6
b. October sample (stations 1, 2, and 7) -
Ortho P Inorganic N Maximum yield
Spike (mg/1) Cone, (mg/1) Cone., (mg/1) (mg/1-dry wt.)
Control
0.050 P
0.050 P + 1.0 N
1.0 N
2. Discussion -
The control yields of the assay alga, Selenastrum capri-
cornutum, indicate that the potential primary productivity
of Glendo Reservoir was moderately high to high in May
(depending on the stations) and moderate in October. Also,
there was a significant growth response in all assays with
the addition of phosphorus alone but no response when only
nitrogen was added. Therefore, phosphorus limitation is
indicated.
The reservoir data support the assay findings. The mean
inorganic nitrogen to orthophosphorus ratios were 25 to 1 in
May, 16 to 1 in August, and 15 to 1 in October. Phosphorus limi-
tation is expected when the N to P ratio is greater than 13 to 1,
-------
IV. NUTRIENT LOADINGS
(See Appendix E for data)
For the determination of nutrient loadings, the Wyoming National
Guard collected monthly near-surface grab samples from each of the
tributary sites indicated on the maps (pages v and vi), except for the high
runoff months of May, June, and July when two samples were collected
at four 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 Wyoming District Office of the U.S. Geological Survey for the
tributary sites nearest the reservoir.
In this report, nutrient loads for sampled tributaries were cal-
culated using mean annual concentrations and mean annual flows. Nutri-
ent loads shown are those measured minus point-source loads, if any.
Nutrient loads for unsampled "minor tributaries and immediate drain-
age" ("ZZ" of U.S.G.S.) were estimated using the means of the concentrations
in Muddy Creek and Willow Creek at stations El and Fl and the mean annual
ZZ flow.
The operator of the Douglas was'tewater treatment plant provided
monthly effluent samples and corresponding flow data. The operator of
the Glendo plant provided effluent samples but could not provide flow
data. Therefore, nutrient loads were estimated at 1.134 P and 3.401
N/capita/year, and flows were estimated at 0.3785 m3/capita/day.
-------
10
A. Waste Sources:
1. Known municipal -
Name
Douglas*
Glendo**
Pop.
Served
Treatment
Mean Flow
(mVd)
2,677 stab, pond 1324.9
210*** trick, filter 79.5
2. Known industrial - (None)
B. Annual Total Phosphorus Loading - Average Year:
1. Inputs -
kg P/
Source y_r
a. Tributaries (non-point load) -
North Platte River 171,200
b. Minor tributaries & immediate
drainage (non-point load)t - 125
c. Known municipal STP's -
Glendo
Douglas
d. Septic tanks"1"1' -
e. Known industrial - None
f. Direct precipitation1"1"'" -
Total
2. Outputs -
240
2,440
945
174,955
Reservoir outlet - North Platte River 49,205
3. Net annual P accumulation - 127,750 kg.
Receiving
Water
North Platte River
Whiskey Gulch
% of
total
97.8
0.1
1.4
0.6
100.0
* Treatment plant questionnaire.
** Anonymous, 1971.
*** 1970 census.
f Includes Whiskey Gulch, Elkhorn Creek, and Cottonwood Creek because
limited numbers of samples were collected from those streams.
tf Estimate based on 10 shoreline dwellings; see Working Paper No. 175.
ttt See working Paper No. 175.
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11
C. Annual Total Nitrogen Loading - Average Year:
1. Inputs -
kg N/ % of
Source yr total
a. Tributaries (non-point load) -
North Platte River 2,182,305 96.8
b. Minor tributaries & immediate
drainage (non-point load)* - 3,070 0.1
c. Known municipal STP's -
Glendo 715 <0.1
Douglas 8,205 0.4
d. Septic tanks** - 105 <0.1
e. Known industrial - None
f. Direct precipitation*** - 58.265 2.6
Total 2,252,665 100.0
2. Outputs -
Reservoir outlet - North Platte 1,742,630
River
3. Net annual N accumulation - 510,035 kg.
D. Non-point Nutrient Export by Subdrainage Area:
Tributary kg P/km2/yr kg N/km2/yr
North Platte River 4 45
* Includes Whiskey Gulch, Elkhorn Creek, and Cottonwood Creek because
limited numbers of samples were collected from those streams.
** Estimate based on 10 shoreline dwellings; see Working Paper No. 175.
*** See Working Paper No. 175.
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12
E. Mean Nutrient Concentrations in Ungaged Streams:
Mean Total P Mean Total N
Tributary -- Cone, (mg/1) Cone, (mg/1)
Muddy Creek 0.068 1.772
Willow Creek 0.084 1.903
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
3.24 2.37 41.7 9.5
Vollenweider phosphorus loadings
(g/m2/yr) based on mean depth and mean
hydraulic retention time of Glendo Reservoir:
"Dangerous" (eutrophic loading) 0.96
"Permissible" (oligotrophic loading) 0.48
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13
V. LITERATURE REVIEWED
Anonymous, 1971. Inventory of municipal waste facilities. EPA Pub.
OWP-1, vol. 8, Wash., DC.
Prior, Roy E, 1974. Personal communication (reservoir morphometry).
WY Dept. of Env. Qual., Cheyenne.
Vollenweider, R.A. and P.O. 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.
-------
14
VI. APPENDICES
APPENDIX A
LAKE' RANKINGS
-------
LA
-------
PERCENT or LAKES WITH HIGHER VALUES (NUMBER OF LAKES WITH HIGHER VALUES)
LAKE
CODE LAKE NAME
5601 BIG CANDY RESERVOIR
5602 BOULDER LAKE
5603 80YSEN RESERVOIR
5604 LAKE DE SMET
5605 FLAMING GORGE RESERVOIR
5606 FREMONT LAKE
5607 GLENDO RESERVOIR
5603 KEY HOLE RESERVOIR
5609 OCEAN LAKE
5610 SEMINOLE RESERVOIR
5611 SODA LAKE
5612 VIVA NAUGHTON RESERVOIR
5613 WOODRUFF NARROWS RESERVO
5614 YELLOWTAIL RESERVOIR
MEDIAN
TOTAL P
0 <
92 (
46 (
54 <
85 (
100 (
31 (
69 1
38 1
62 1
23 i
15 I
8 i
77
0)
; 12)
: 6)
: 7)
: ID
: 13)
! 4)
: 9)
1 5)
I 8)
! 3)
( 2)
t 1)
( 10)
MEDIAN
INORG N
54 (
92 <
23 <
73 <
0 <
73 (
8 1
62 <
92 <
31 I
92 '
33 <
46 <
15
7)
: ii)
; 3)
: 9)
: o)
: 9)
i i)
; 8>
! 11)
! 4)
( 11)
[ 5)
( 6)
( 2)
500-
MEAN SEC
0 (
92 (
23 (
62 <
77 1
100 (
31 1
38 (
8 I
46 1
69 i
54 <
15 i
85
: o>
12)
: 3)
: e)
: 10)
: 13)
: 4)
; 5)
i i)
[ 6)
: 9)
[ 7)
( 2)
( 11)
MEAN
CHLORA
77 (
100 (
46 <
15 (
54 (
8b <
23 1
31 (
38 (
92 (
62 I
0 1
8 <
69
10)
13)
! 6)
! 2)
i 7)
: ID
: 3>
; 4)
! 5)
: 12)
[ 8)
! 0)
f 1)
( 9)
15-
MIN DO
77 <
92 (
8 (
69 <
46 (
100 <
38 1
15 1
as i
54 1
0 <
27 (
27 i
62
10)
: 12)
: i>
: 9)
: 6)
; 13)
: 5)
: 2)
i ID
[ 7)
t 0)
[ 3)
! 3)
( 8)
MEDIAN
DISS ORTHO P
8 (
92 <
42 <
62 <
85 <
100 (
42 <
69 (
77 (
54 1
31 1
0 1
15 1
23 i
1)
12)
5)
: 8)
11)
13)
: 5)
; 9)
: 10)
: 7)
; 4)
: o>
: 2)
( 3)
INOEX
NO
216
560
Id8
335
347
558
173
284
338
339
277
134
119
331
-------
LAKES RANKED BY INDEX NOS.
RANK LAKE CODE LAKE NAME
INDEX NO
1 5602 BOULDER LAKE 560
2 5606 FREMONT LAKE 558
3 5605 FLAMING GORGE RESERVOIR 347
4 5610 SEMINOLE RESERVOIR 339
5 5609 OCEAN LAKE 338
6 5604 LAKE DE SMET 335
7 5614 YELLOWTAIL RESERVOIR 331
8 5608 KEY HOLE RESERVOIR ?84
9 5611 SODA LAKE 277
10 5601 BIG SANOY RESERVOIR 216
11 5603 BOYSEN RESERVOIR 188
12 5607 GLENDO RESERVOIR 173
13 5612 VIVA NAUGHTON RESERVOIR 134
14 5613 WOODRUFF NARROWS RESERVO 119
-------
APPENDIX B
CONVERSION FACTORS
-------
CONVERSION FACTORS
Hectares x 2.471 = acres
Kilometers x 0.6214 = miles
Meters x 3.281 = feet
Cubic meters x 8.107 x 10 = 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 WYOMING
08/05/76
LAKE CODE 5607 GLENDO RESERVOIR
TOTAL DRAINAGE AREA OF LAKE(SO KM) 50523.1
SUB-DRAINAGE
TRIBUTARY AREAiSQ KM)
JAN
FEB
MAR
APR
NORMALIZED FLOWS(CMS)
MAY JUN JUL AUG
SEP
OCT
NOV
OEC
MEAN
5607A1
5607A2
5607B1
560701
5607G1
5607ZZ
50523.1
48813.7
25.9
150.2
64.7
1476.3
0.59
26.22
0.0
0.0
0.0
0.028
2.97
29.48
0.0
0.0
0.0
0.028
13.85
32.71
0.028
0.028
0.014
0.028
27.38
53.63
0.028
0.028
0.028
0.028
61.50
92.23
0.028
0.028
0.028
0.057
70.00
75.95
0.0
0.0
0.0
0.057
128.56
50.74
0.0
0.0
0.0
0.028
137.34 71.47
46.13 36.84
0.0 0.0
0.0 0.0
0.0 0.0
0.028 0.028
1.42
32.37
0.0
0.0
0.0
0.028
0.23
61.79
0.0
0.0
0.0
0.028
0.68
26.25
0.0
0.0
0.0
0.028
43.34
47.06
0.007
0.007
0.006
0.033
SUMMARY
TOTAL
SUM OF
DRAINAGE
AREA OF
LAKE =
SUB-DRAINAGE AREAS
50523.1
50530.9
TOTAL FLOW IN =
TOTAL FLOW OUT =
564.
515.
96
99
MEAN MONTHLY FLOWS AND DAILY FLOWS(CMS)
TRIBUTARY MONTH YEAR MEAN FLOW DAY
5607A1
FLOW DAY
FLOW DAY
FLOW
5607A2
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
0.198
0.057
0.057
0.085
0.113
0.481
25.995
73.709
72.208
149.796
146.398
86.933
37.661
39.077
33.414
26.335
31.149
29.166
42.475
63.147
63.996
52.952
83.252
71.075
7
4
6
3
3
8
. 5
S
7
4
7
4
3
3
8
5
8
7
4
0.255
0.057
0.170
0.085
40.210
62.580 21
88.065 25
173.016 25
146.964
130.257
37.945
39.360
39.360
39.644
41.626 21
71.358 25
53.802 25
52.952
109.303
102.790
82.402
144.699
83.535
62.297
53.802
-------
TRIBUTARY FLO* INFORMATION FUR WYOMING 08/05/7b
LAKE CODE 5607 GLENDO RESERVOIR
MEAN MONTHLY FLOWS AND DAILY FLOWS(CMS)
TRIBUTARY MONTH YEAR MEAN FLOW DAY FLOW DAY FLOW DAY FLOW
560781
5607D1
5607G1
5607ZZ
10
11
12
1
2
3
4
5
6
7
a
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
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.028
0.028
0.023
0.028
0.028
0.028
0.028
0.028
0.028
0.023
0.028
0.028
-------
APPENDIX D
PHYSICAL and CHEMICAL DATA
-------
STORE! RETRIEVAL DATE 76/08/05
DATE
FROM
TO
75/05/22
75/08/27
75/10/14
00010
TIME DEPTH WATER
OF TEMP
DAY FEET
14
14
14
14
11
11
11
11
11
12
12
12
12
40
40
40
40
55
55
55
55
55
10
10
10
10
0000
0005
0015
0028
0000
0005
0015
0040
0066
0000
0005
0015
0031
CENT
11.3
10.9
10.3
10.1
20.5
20.0
19.9
19.2
18.2
12.5
12.5
12.4
12. 4
560701
42 28 38.0 104 57
GLENDO RESERVOIR
56031 WYOMING
12.0 3
090991
HEPALES
211
0032 FEET DEPTH CLASS
00300
DO
MG/L
9.8
9.4
9.4
9.2
5.8
6.2
5.2
3.6
2.4
6.8
7.8
7.6
7.4
00077
TRANSP
SECCHI
INCHES
144
16
24
00094
CNDUCTVY
FIELD
MICROMHO
564
555
548
544
567
559
551
539
539
502
502
507
525
00400
PH
SU
8.50
8.55
8.60
8.60
8.10
8.30
8.25
8.15
8.00
8.20
8.25
8.30
8.30
00410
T ALK
CAC03
MG/L
155
155
154
156
156
142
143
146
148
152
151
151
151
00610
NH3-N
TOTAL
MG/L
0.090
0.080
0.080
0.080
0.040
0.030
0.060
0.180
0.340
0.130
0.140
0.140
0.140
1202
00
00625
TOT KJEL
N
MG/L
0.800
0.500
0.400
0.500
0.200
0.300
0.400
0.500
0.900
0.400
0.400
0.500
0.400
00630
N02&N03
N-TOTAL
MG/L
0.280
0.260
0.280
0.280
0.140
1.000
0.16C
0.190
0.180
0.140
0.140
0.140
0.150
00671
PHOS-OIS
ORTHO
MG/L P
0.007
0.008
0.007
0.008
0.018
0.012
0.018
0.035
0.053
0.017
0.019
0.017
0.018
DATE TIME DEPTH
FROM OF
TO DAY FEET
75/05/22 14 40 0000
14 40 0005
14 40 0015
14 40 0028
75/08/27
55 0000
55 0005
55 0015
55 0040
55 0066
75/10/14 12 10 0000
12 10 0005
12 10 0015
12 10 0031
0665
iS-TOT
./L P
0.031
0.031
0.035
0.056
0.039
0.034
0.039
0.062
0.092
0.045
0.039
0.039
0.038
32217
CHLRPHYL
A
UG/L
2.8
3.7
5.5
00031
INCDT LT
REMNING
PERCENT
-------
STORET RETRIEVAL DATE 7&/08/U5
DATE TIME DEPTH WATER
FROM OF
TO DAY FEET
75/05/23 15 00 0000
15 00 0005
15 00 0025
15 00 0048
15 00 0072
75/08/27 13 30 0000
13 30 0005
13 30 0015
13 30 0038
75/10/14 12 40 0000
12 40 0005
12 40 0016
DATE TIME DEPTH
FROM OF
TO DAY FEET
75/05/22 15 00 0000
15 00 0005
15 00 0025
15 00 0048
15 00 0072
75/08/27 13 30 0000
13 30 0005
13 30 0015
13 30 0038
75/10/14 1? 40 0000
12 40 0005
12 40 0016
560702
42 31 52.0 104 58 32.0 3
GLENDO RESERVOIR
56031 WYOMING
090991
11EPALES 2111202
0076 FEET DEPTH CLASS 00
0010 00300 00077 00094
TER DO TRANSP CNDUCTVY
EMP SECCHI FIELD
ENT
10.9
10.1
9.d
8.9
7.2
21.0
19.7
19.4
17.8
12.0
12.0
1 l.y
OboS
S-TOT
/L f
0.030
0.045
0.034
0.024
0.030
0.073
0.054
0.050
0.054
0.045
0.053
0.045
MG/L
9
9
9
9
9
9
7
7
6
6
7
7
3221
INCHES MICROMHO
.8 120
.6
.3
.6
.8
.0 15
.8
.2
.0
.6 20
.6
.4
7 00031
530
532
519
532
519
558
557
560
524
515
533
520
00400 0041U
PH T ALK
CAC03
su
8
8
8
8
8
8
8
8
8
8
8
8
.60
.60
.60
.60
.65
.70
.60
.60
.30
.40
.45
.05
MG/L
148
156
153
156
150
143
144
145
144
153
152
153
00610 00625 00630 00671
NH3-N TOT KJEL N02&N03 PHOS-DIS
TOTAL N N-TOTAL ORTHO
MG/L
0.060
0.060
0.060
0.060
0.060
0.020
0.020
0.030
0.090
0.090
0.080
0.080
MG/L
0
0
0
0
0
0
0
0
0
0
0
0
.600
.600
.500
.400
.500
.900
.600
.500
.600
.400
.500
.500
MG/L
0.260
0.260
0.270
0.230
0.260
0.060
0.080
0.110
0.220
0.100
0.100
0.100
MG/L P
0.006
0.006
0.005
0.005
0.005
0.016
0.010
0.012
0.020
0.012
0.016
0.012
CHLRPHYL INCDT LT
A
UG/L
3
26
8
REMNING
PERCENT
.6
.3
.9
-------
STORET RETRIEVAL DATE 76/08/05
560703
42 34 27.0 100 57 18.0 3
GUBMOO i&ESER V 01R
5^31 WYOMING
090991
11EPALES 2111202
0030 FEET DEPTH CLASS 00
DATE
FROM
TO
75/05/22
DATE
FROM
TO
75/05/22
TIME DEPTH
OF
DAY FEET
15 25 0000
15 25 0005
15 25 0015
15 25 0026
TIME DEPTH
OF
DAY FEET
15 ?5 0000
15 25 0005
15 25 0015
15 25 0026
00010
HATER
TEMP
CENT
10. a
10.2
9.6
8.9
00665
PHOS-TOT
MG/L P
0.038
0.031
0.029
0.05*
00300
DO
MG/L
10.0
9.8
9.6
9.6
32217
CHLRPHYL
A
UG/L
7.2
00077
TRANSP
SECCHI
INCHES
63
00031
INCDT LT
REMNING
PERCENT
00094
CNDUCTVY
FIELD
MICROMHO
513
525
527
522
00400
PH
SU
8.65
8.70
8.65
8.70
00410
T ALK
CAC03
MG/L
141
148
149
147
00610
NH3-N
TOTAL
MG/L
0.040
0.040
0.040
0.040
00625
TOT KJEL
N
MG/L
0.500
0.400
0.500
0.400
00630
N02&N03
N-TOTAL
MG/L
0.250
0.160
0.170
0.170
00671
PHOS-DIS
ORTHO
MG/L P
0.005
0.003
0.002
0.005
-------
STORE! RETRIEVAL DATE 76/08/05
560704
42 34 11.0 105 02 27.0 3
GLEMDO RESERVOIR
56031 WYOMING
090991
DATE
FROM
TO
75/05/32
DATE
FROM
TO
75/05/2?
TIME DEPTH
OF
DAY FEET
15 40 0000
15 40 0005
15 40 0015
15 40 0022
TIME DEPTH
OF
DAY FEET
15 40 0000
15 40 0005
15 40 0015
15 40 0022
00010
WATER
TEMP
CENT
12.5
11.5
10.8
10.5
00665
PHOS-TOT
MG/L P
0.072
0.371
0.077
0.070
00300
00
MG/L
9.4
8.4
ft. 4
P. 4
32217
CHLRPHYL
A
UG/L
5.8
00077
TRANSP
SECCHI
INCHES
21
00031
INCDT LT
REMNING
PERCENT
00094
CNDUCTVY
FIELD
MICROMHO
436
418
382
355
11EPALES
0026
00400
PH
SU
8.50
8.45
8.40
8.45
211
FEET DEPTH CLASS
00410
T ALK
CAC03
MG/L
124
124
118
124
00610
NH3-N
TOTAL
MG/L
0.050
0.050
0.050
0.050
1202
00
00625
TOT KJEL
N
MG/L
0.500
0.400
0.400
0.400
00630
N02&.N03
N-TOTAL
MG/L
0.300
0.300
0.300
0.300
00671
PHOS-DIS
ORTHO
MG/L P
0.023
0.024
0.026
0.023
-------
STORET RETRIEVAL DATE 76/08/05
560705
42 36 22.0 105 04 50,
GLENDO RESERVOIR
56031 WYOMING
0 3
090991
11EPALES 2111202
0016 FEET DEPTH CLASS 00
DATE
FROM
TO
75/05/22
DATE
FROM
TO
75/05/22
TIME DEPTH
OF
DAY FEET
16 00 0000
16 00 0005
16 00 0012
TIME DEPTH
OF
DAY FEET
16 00 0000
16 00 0005
16 00 0012
00010
WATER
TEMP
CENT
9.0
9.0
8.6
00665
PHOS-TOT
MG/L P
0.139
0.248
0.147
00300
DO
MG/L
8.2
9.2
9.8
32217
CHLRPHYL
A
UG/L
4.6
00077
TRANSP
SECCHI
INCHES
10
00031
INCDT LT
REMNING
PERCENT
00094
CNDUCTVY
FIELD
MICROMHO
310
310
312
00400
HH
SU
8.30
8.25
8.30
00410
T ALK
CAC03
MG/L
101
103
110
00610
NH3-N
TOTAL
MG/L
0.040
0.050
0.050
00625
TOT KJEL
N
MG/L
0.600
0.400
0.300
00630
N02&N03
(M-TOTAL
MG/L
0.360
0.370
0.340
00671
PHOS-OIS
ORTHO
MG/L P
0.034
0.033
0.028
-------
STORET RETRIEVAL DATE 76/08/05
560706
42 33 54.0 104 58 20.0 3
GLENDO RESERVOIR
56031 WYOMING
DATE TIME DEPTH
FROM OF
TO DAY FEET
75/08/27 14 00 0000
00010
WATER
TEMP
CENT
18.0
00300 00077 00094
DO TRANSP CNDUCTVY
SECCHI FIELD
MG/L INCHES MICROMHO
11EPALES 760109 2111202
0999 FEET DEPTH CLASS 00
6.2
480
00400
PH
SU
8.25
00410
T ALK
CAC03
MG/L
142
OOblO
NH3-N
TOTAL
MG/L
0.090
00625
TOT KJEL
N
MG/L
0.600
00630
N02&N03
N-TOTAL
MG/L
0.300
00671
PHOS-OIS
ORTHO
MG/L P
0.016
00665 32217 00031
DATE TIME DEPTH PHOS-TOT CHLRPHYL INCDT LT
FROM OF A REMNING
TO DAY FEET MG/L P UG/L PERCENT
75/08/27 14 00 0000
0.055
10.5
-------
STORE! RETRIEVAL DATE 76/08/05
560707
42 3J 38.0 104 56 36.0 3
GLENOO RESERVOIR
56031 WYOMING
11EPALES 760109 2111202
0005 FEET DEPTH CLASS 00
DATE TIME DEPTH
FROM OF
TO DAY FEET
75/10/14 13 00 0000
DATE
FROM
TO
OF
DAY
FEET
75/10/14 13 00 0000
00010
WATER
TEMP
CENT
10.1
00665
'HOS-TOT
MG/L P
0.042
00300
DO
MG/L
8.0
32217
ChLRPHYL
A
UG/L
14.3
00077 00094
TRANSP CNOUCTVY
SECCHI FIELD
INCHES MICPOMHO
12 486
00031
INCDT LT
REMN1NG
PERCENT
00400 00410
PH T ALK
CAC03
SU M6/L
8.40 155
00610
NH3-N
TOTAL
MG/L
0.030
00625 00630
TOT KJEL N02iN03
N N-TOTAL
MG/L MG/L
0.400 0.050
00671
PHOS-OIS
ORTMO
MG/L P
0.007
-------
APPENDIX E
TRIBUTARY and WASTEWATER
TREATMENT PLANT DATA
-------
STORET RETRIEVAL DATE 76/08/05
5607A1
42 27 30.0 104 56 45.0 4
N PLATTE RIVER
56 7.5 CASSA
O/GLENDO RESERVOIR 090991
BNK FRM UNPVD RD 1 MI SE OF POWERHOUSE
11EPALES 2111204
0000 FEET DEPTH CLASS 00
DATE
FROM
TO
74/10/07
74/11/04
75/02/06
75/03/03
75/04/03
75/05/08
75/05/21
75/06/05
75/06/25
75/07/08
75/07/25
75/08/07
75/09/04
00630 00625
TIME DEPTH N02&N03 TOT KJEL
OF N-TOTAL N
DAY FEET
13
14
13
10
14
10
11
11
10
13
14
13
10
05
30
40
55
40
35
40
?5
35
31
30
15
30
MG/L
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
040
072
416
420
330
332
280
250
260
210
160
170
080
MG/L
1.
1.
1.
0.
0.
0.
0.
0.
1.
0.
1.
1.
1.
200
600
000
750
650
600
300
800
900
900
150
200
500
00610 00671 00665
NH3-N PHOS-OIS PHOS-TOT
TOTAL ORTHO
MG/L
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
020
046
056
020
070
021
045
230
095
080
085
030
045
MG/L
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
G.
0.
P
005
025
016
015
010
015
010
037
025
020
020
010
010
MG/L P
0.015
0.050
0.030
0.020
0.040
0.030
0.020
0.040
0.039
0.030
0.040
0.040
0.070
-------
STORE! RETRIEVAL DATE 76/08/05
DATE TIME DEPTH NC
FROM OF N=
TO DAY FEET
74/10/07
74/11/04
74/12/03
75/03/03
75/05/08
75/05/21
75/06/05
75/06/25
75/07/08
75/07/25
75/08/07
75/09/04
08 00
10 45
09 30
09 45
09 15
10 30
08 45
09 25
16 25
15 35
15 25
09 00
5607A2
42 41 02.0 105 09 50.0 4
N PLATTE RIVER
56 7.5 ORIN
T/GLENDO RESERVOIR 090991
FROM BRDG 1 MI EbE ORIN JCT ON US RT 87
11EPALES 2111204
0000 FEET DEPTH CLASS 00
0630
'&N03
OTAL
G/L
C.336
0.720
0.480
0.560
0.315
0.270
0.330
08140
0.165
0»210
Oo045
0,270
00625
TOT KJEL
N
MG/L
0.800
1.000
1.150
0.750
1.000
0.850
1.400
1.600
1.900
1.200
0.625
1,400
00610
IMH3-N
TOTAL
MG/L
0.015
0.035
0.020
0.040
0.025
0.021
0.030
0.040
0.040
0.025
0.025
0.020
00671
PHOS-DIS
ORTHO
MG/L P
0.010
0.035
0.030
0.065
0.045
0.052
0.040
0.015
0.025
0.030
0.015
0.035
00665
PHOS-TOT
MG/L P
0.025
0.070
0.065
0.130
0.110
0.240
0.150
o.oao
0.170
0.130
0.095
0.140
-------
STORE! RETRIEVAL DATE 76/08/05
00630
DATE TIME DEPTH N02&N03
FROM OF N-TOTAL
TO DAY FEET MG/L
75/05/08 08 30
75/05/21 11 10
75/07/35 14 45
0.015
0.020
00635 00610
TOT KJEL NH3-N
N TOTAL
MG/L MG/L
4.600
5.750
4.800
0.045
0.135
5607bl
42 29 10.0 105 00 40.0 4
WHISKEY GULCH
56 7.5 SIBLEY PEAK
T/GLENDO RESERVOIK 090991
bRDG ON SIOUX SHORELINE DRIVE
11EPALES 2111204
0000 FEET DEPTH CLASS 00
00671 00665
PHOS-DIS PHOS-TOT
ORTHO
MG/L P MG/L P
0.090
0.500
0.480
1.250
0.780
-------
STORET RETRIEVAL DATE 76/08/05
00b30
DATE TIME DEPTH N02&.N03
FROM OF N-TOTAL
TO DAY FEET MG/L
75/05/08 09 35
75/05/21 10 50
0.037
0.060
00625
TOT KJEL
N
MG/L
0.400
0.100
00610
NH3-N
TOTAL
MG/L
0.017
0.015
00671
PHOS-DIS
ORTHO
MG/L P
0.010
0.010
560701
42 34 35.0 105 04 15.0 4
ELKHO^N CREEK
56 7.5 GLEN00
T/GLENDO RESERVOIR 090991
100 FT FRM END DIRT RD 6 MI NNW GLENDO
11EPALES 2111204
0000 FEET DEPTH CLASS 00
00665
PHOS-TOT
MG/L P
0.010
0.010
-------
STORE! RETRIEVAL DATE 76/08/05
DATE TIME DEPTH N02MM03
FROM OF
TO DAY FEET
74/10/07
74/11/0^
74/12/03
75/01/02
75/02/06
75/03/03
75/04/03
75/05/08
75/05/21
75/06/05
75/06/25
75/07/Ofl
75/07/25
75/08/07
75/09/04
12
13
10
10
14
11
11
14
14
10
11
11
13
14
11
10
55
45
20
20
40
35
00
05
20
40
35
50
20
15
5607E1
42 36 08.0 100 56 25.0 4
MUDDY CREEK
56 7.5 JEWEL SPRNGS
T/GLENDO RESERVOIR 090991
OIRT rtD 8KDG 5.5 MI NNW FROM END PAVEMNT
11EPALES 2111204
0000 FEET DEPTH CLASS 00
0630 00625
&N03 TOT KJEL
OTAL N
G/L MG/L
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
.016
.056
.256
.384 C
.408
.200
.900
.900
.900
.800
.100
.100
.165 2.100
.035 ]
.000
.010 0.700
.010 ]
.010
1.530
1.800
.015 2.300
.015 3.150
.005
1.100
.010 2.600
00610 00671 0066S
NH1-N PHOS-OIS PHOS-TOT
TOTAL ORTHO
MG/L
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
.027
.060
.065
.072
.128
.075
.070
.025
,020
.030
.030
.050
.065
.030
.040
MG/L P
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
.012
.020
.020
.030
.048
.060
.035
.030
.010
.033
.010
.025
.045
.010
.015
MG/L
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
•
•
•
•
•
•
•
•
•
•
•
•
•
•
•
P
045
050
040
050
100
120
090
050
050
045
040
060
120
060
100
-------
STORE! RETRIEVAL DATE 76/08/05
DATE TIME DEPTH
FROM OF
TO DAY FEET
74/10/07
74/11/04
74/12/03
75/02/06
75/03/03
75/04/03
75/05/08
75/05/21
75/06/05
75/06/25
75/07/08
75/07/25
75/08/07
11 57
13 30
10 25
14 35
11 55
11 ?0
13 40
13 50
10 00
11 20
11 17
13 35
14 15
5607F1
42 35 09.0 104 55 37.0 4
KILLOW CREEK
56 7.5 JEWEL SPRNGS
T/GLENDO RESERVOIR 090991
BROG .8 MI W RUINS 2.8 MI NNW END PAVMNT
11EPALES 2111204
0000 FEET DEPTH CLASS 00
0630
:6.N03
OTAL
iG/L
0.032
0.016
0.032
0.376
0.025
0.020
0.010
0.015
0.020
0.005
0.020
0.010
0.010
00625
TOT KJEL
N
MG/L
2.000
1.000
1.500
1.400
1.100
1.900
1.300
1.500
1.050
2.900
4.100
2.100
2.300
00610
NH3-N
TOTAL
MG/L
0.090
0.360
0.030
0.116
0.035
0.050
0.030
0.040
0.030
0.050
0.115
0.075
0.055
00671
PHOS-DIS
ORTHO
MG/L P
0.03S
0.030
0.005
0.016
0.020
0.015
0.030
0.010
0.045
0.010
0.060
0.020
0.015
00665
PHOS-TOT
MG/L P
0.095
0.040
0.020
0.030
0.050
0.050
0.060
0.070
0.070
0.080
0.270
0.180
0.080
-------
STORET RETRIEVAL DATE 76/08/05
5607G1
42 31 55.0 104 54 40.0 4
COTTONWOOD CREEK
56 7.5 JEWEL SPRNGS
T/GL£rtDO RESERVOIR 090991
CNTr RO BRDG .3 MI W OF CRANDALL DAM
11EPALES 3111204
0000 FEET DEPTH CLASS 00
DATE TIME DEPTH N02&N03
FROM OF
TO DAY FEET
75/03/03 11 20
75/04/03 10 55
75/05/03 13 20
75/05/21 13 30
75/06/05 09 45
0630
I&N03
OTAL
IG/L
0.095
0.005
0.005
0.020
0.005
00625
TOT KJEL
N
MG/L
2.400
1.200
0.675
0.750
1.000
00610
NH3-N
TOTAL
MG/L
0.075
0.085
0.025
0.025
0.020
00671
PHOS-DIS
ORTHO
MG/L P
0.210
0.045
0.060
0.100
0.053
00665
PHOS-TOT
MG/L P
0.370
0.080
0.060
0.120
0.120
-------
STORET RETRIEVAL DATE 76/08/05
00630
DATE TIME DEPTH N02fcN03
FROM OF N-TOTAL
TO DAY FEET MG/L
75/02/10 14 30
75/04/10 15 30
75/05/08 11 00
75/06/09 15 00
75/07/08 14 00
75/07/28 14 00
75/09/25 14 00
0.080
0.020
0.050
0.200
0.150
0.175
0.075
00625
TOT KJEL
N
MG/L
26.600
19.000
20.000
16.000
5.900
13.500
17.000
00610
NH3-N
TOTAL
MG/L
13.900
6.700
0.260
0.790
0.130
0.150
0.230
5607AA PD5607AA P002677
42
-------
STORE! RETRIEVAL DATE 76/08/05
DATE
FROM
TO
75/02/07
CP(T>-
75/02/07
75/03/21
CP(T)-
75/03/21
75/04/25
CP(T)-
75/04/25
75/07/24
75/08/20
CP(T>-
75/08/20
75/09/08
CP(T>-
75/09/08
75/10/30
CP(T>-
75/10/30
75/12/05
CP(T>-
75/12/05
00630
TIME DEPTH N02&N03
OF N-TOTAL
DAY FEET MG/L
11
16
08
12
11
15
08
15
08
14
08
12
08
13
00
00
00
00
00
00
00
00
00
00
00
00
00
00
0
0
0
1
0
0
0
0
.030
.160
.300
.000
.026
.200
.175
.250
00625
TOT KJEL
N
MG/L
42.
44.
90.
49.
48.
55.
69.
61.
000
000
000
000
000
000
000
000
5607BA PK5607BA P000210
42 30 00.0 105 01 30.0 4
GLENDO
56 7.5 GLENDO
T/GLENDO RES. 090991
WHISKEY GULCH
11EPALES 2141204
0000 FEET DEPTH CLASS 00
00610 00671 00665 50051 50053
NH3-N PHOS-OIS PHOS-TOT FLO* CONDUIT
TOTAL ORTHO RATE FLOW-MGO
MG/L MG/L P MG/L P INST MGO MONTHLY
38.000
34.000
35.000
36.000
7.900
9.000
5.700 13.000
28.800 6.300 21.000
31.000 10.000 14.000
29.000 8.700 12.000
9.600 16.500
41.000 11.500 15.000
9.600 13.000
------- |