U.S. ENVIRONMENTAL PROTECTION AGENCY
NATIONAL EUTROPHICATION SURVEY
WORKING PAPER SERIES
CORVALLIS ENVIRONMENTAL RESEARCH LABORATORY - CORVALLIS, OREGON
and
ENVIRONMENTAL MONITORING & SUPPORT LABORATORY - LAS VEGAS, NEVADA
699-440
-------
REPORT
ON
BOYSEN RESERVOIR
FR0WT COUNTY
WYOMING
EPA mm viii
WORKING PAPER No, 883
WITH THE COOPERATION OF THE
WYOMING DEPARTMENT OF ENVIRONMENTAL
AND THE
WYOMING NATIONAL GUARD
JULY, 1977
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CONTENTS
Page
Foreword ii
List of Wyoming Lakes and 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 9
V. Literature Reviewed 15
VI. Appendices . 16
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FOREWORD
The National Eutrophication Survey was initiated in 1972 in
response to an Administration commitment to investigate the nation-
wide threat of accelerated eutrophication to freshwater lakes and
reservoirs.
OBJECTIVES
The Survey was designed to develop, in conjunction with state
environmental agencies, information on nutrient sources, concentrations,
and impact on selected freshwater lakes as a basis for formulating
comprehensive and coordinated national, regional, and state management
practices relating to point-source discharge reduction and non-point
source pollution abatement in lake watersheds.
ANALYTIC APPROACH
The mathematical and statistical procedures selected for the
Survey's eutrophication analysis are based on related concepts that:
a. A generalized representation or model relating
sources, concentrations, and impacts can be constructed.
b. By applying measurements of relevant parameters
associated with lake degradation, the generalized model
can be transformed into an operational representation of
a lake, its drainage basin, and related nutrients.
c. With such a transformation, an assessment of the
potential for eutrophication'control can be made.
LAKE ANALYSIS
In this report, the first stage of evaluation of lake and water-
shed data collected from the study lake and its drainage basin is
documented. The report is formatted to provide state environmental
agencies with specific information for basin planning [§303(e)], water
quality criteria/standards review [§303(c)]» clean lakes [§314(a,b)],
and water quality monitoring [§106 and §305(b)] activities mandated
by the Federal Water Pollution Control Act Amendments of 1972.
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m
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
Yel'lowtail
IV
NATIONAL EUTROPHICATION 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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BOYSEN RESERVOIR
Tributary Sampling Site
X Lake Sampling Site
Sewage Treatment Facility
-------
BOYSEN RESERVOIR
STORE! NO. 5603
I. CONCLUSIONS
A. Trophic Condition:
Survey data indicate that Boysen Reservoir is eutrophic. It
ranked eleventh in overall trophic quality when the 14 Wyoming
lakes and reservoirs sampled in 1975 were compared using a com-
bination of six water quality parameters*. Seven of the water
bodies had less median total phosphorus, seven had less and two
had the same median dissolved orthophosphorus, ten had less median
inorganic nitrogen, seven had less mean chlorophyll a_, and ten
had greater mean Secchi disc transparency. Marked depression of
dissolved oxygen with depth occurred at station 4 in September.
Survey limnologists noted surface clumps of algae at various
stations in September and October.
B. Rate-Limiting Nutrient:
The algal assay results are not considered representative of
conditions in the reservoir at the time the samples were
collected (05/19/75 and 10/17/75) due to significant changes in
the nutrient levels in the samples during shipment from the field
to the laboratory.
The reservoir data indicate nitrogen limitation at all sampling
stations and times, with the exception of station 2 in May and sta-
tion 4 in September.
* See Appendix A.
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2
C. Nutrient Controllability:
1. Point sources—During the sampling year, known point
sources accounted for 5.8% of the total phosphorus load to Boy-
sen Reservoir. The wastewater treatment plant at Riverton con-
tributed 3.0%. The facilities at Shoshoni, Hudson, and Lander
were estimated to have contributed 0.2%, 0.1%, and 2.5%, respec-
tively, but further investigation would be needed to determine
the actual contribution of those sources.
The present loading of 3.56 g/m2/year is five times that pro-
posed by Vollenweider (Vollenweider and Dillon, 1974) as a eutro-
phic loading (see page 14). It is calculated that an 80% reduction
of the phosphorus load would be required to lower the loading to
the eutrophic level. This would involve control of non-point as
well as point-source phosphorus inputs.
2. Non-point sources--Non-point sources contributed 94.2%
of the total phosphorus loading during the sampling year. The
Wind River contributed 77.4%, Fivetnile Creek contributed 7.7%, and
six other gaged tributaries collectively contributed 4.8%. The
ungaged minor tributaries and immediate drainage contributed an
estimated 3.8%.
The phosphorus export rates of Fivemile Creek and the Wind
River, 23 kg and 22 kg/km2/year, were substantially greater than
the rates of the other tributaries of the reservoir (mean of 3 kg/
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3
km2/year; see page 13). This may be indicative of unknown
point sources, underestimation of point source loads, or sub-
stantial inputs from non-point sources. For Fivemile Creek,
part of the high export rate is due to the outflow of eutrophic
Ocean Lake* and drainage from surrounding agricultural lands.
Further investigation is needed to determine the controllability
of nutrients from non-point sources within the Wind River and
Fivemile Creek drainages.
* Working Paper No. 889.
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II. RESERVOIR AND DRAINAGE BASIN CHARACTERISTICS1"
A. Morphometry :
1. Surface area: 89.84 kilometers2.
2. Mean depth: 10.4 meters.
3. Maximum depth: 39.6 meters.
4. Volume: 934.336 x 106 m3.
5. Mean hydraulic retention time: 270 days (based on outflow).
B. Tributary and Outlet:
(See Appendix C for flow data)
1. Tributaries -
Drainage Mean flow
Name area (km2)* (m3/sec)*
Wind River 11,370.1 39.900
Badwater Creek 2,092.7 0.650
Ditch D-l - 0.040
Ditch E-l - 0.059
Fivemile Creek 1,082.6 4.200
Muddy Creek 859.9 0.531
Wyoming Canal - 0.119
Cottonwood Creek 427.3 0.055
Minor tributaries &
immediate drainage - 4,023.2 0.163
Totals 19,855.8 45.717
2. Outlet -
Wind River 19,945.6** 40.000
C. Precipitation***:
1. Year of sampling: 23.3 centimeters.
2. Mean annual: 21.7 centimeters.
t Table of metric conversions—Appendix B.
tt Martin and Hanson, 1966.
* For limits of accuracy, see Working Paper No. 175, "...Survey Methods,
1973-1976".
** Includes area of reservoir.
*** See Working Paper No. 175.
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5
III. WATER QUALITY SUMMARY
Boysen Reservoir was sampled three times during the open-water
season of 1974 by means of a pontoon-equipped Huey helicopter. Each
time, samples for physical and chemical parameters were collected
from a number of depths at four stations on the reservoir in May
and five stations in September and October (see map, page v). During
each visit, a single depth-integrated (4.6 m or near bottom to surface)
sample was composited from the stations for phytoplankton identification
and enumeration; and during the first and last visits, a single 18.9-
liter depth-integrated sample was composited for algal assays. Also
each time, a depth-integrated sample was collected from each of the
stations for chlorophyll ^analysis. The maximum depths sampled
were 4.6 meters at station 1, 15.8 meters at station 2, 16.8 meters
at station 3, 29.9 meters at station 4, and 1.5 meters at station 5.
The sampling results are presented in full in Appendix D and
are summarized in the following table.
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PARAMETER
TEMP
DISS OXY (MG/L)
CNOCTVY (MCROMO)
Pri (STAMD UNITS)
TOT ALK (MG/L)
TOT P (MG/L)
ORTHO P (MG/L)
N02*N03 (MG/L)
AMMONIA (MG/L)
KJEL N (MG/L)
INORG N (MG/L)
TOTAL N (MG/L)
CHLRPYL A (Ufi/L)
SECCHI (METERS)
A. SU •'•"•' A^Y >> -
1ST SAMPLING (
*
7.1
7.4
DOO.
8.2
157.
0.021
0.007
0.060
0.030
0.200
0.090
0.350
8.7
0.2
4
ANGE
- 14.2
- 11. C
619.
8.8
175.
- 0.10C
- 0.024
- 0.180
- 0.100
- 0.700
- 0.280
- 0.850
- 13.6
1.5
SITES
MEAN
11.0
9.0
557.
8.5
165.
0.040
0.014
0.128
0.049
0.480
0.177
0.60-3
10.6
0.8
HYSICAL AND CHEMICAL CHARACTERISTICS FOK
STGRET CODE 5603
5/19/75)
MEDIAN
11.3
9.0
555.
8.5
165,
0.031
0.014
0. 140
0.05U
0.500
0.190
0.640
10.1
o.«
2ND
RANGE
14.5 -
0.6 -
^15. -
7.8 -
111. -
0.017 - 0
0.004 - 0
0.020 - 1
0.020 - 0
0.200 - 0
0.040 - 1
0.240 - 1
2.0 -
0.3 -
SAMPLING ( 9/
5
20.3
7.6
567.
8.7
166.
.264
.062
= 400
.070
.600
.420
.600
13.0
1.5
SITES
MEAN
19.3
6.3
462.
8.4
125.
0.051
0.012
0.129
0.025
0.338
0.153
0.467
6.7
1.0
BOfSEN «E5
2/75)
MEDIAN
19.8
7.0
430.
8.6
118.
0.030
0.008
0.040
0.020
0.300
0.060
0.420
4.3
1.4
iE&vOIR
3RD
RANGE
11.4 -
7.6 -
426.
8.1 -
118. -
0.032 - 0
0.006 - 0
0.020 - 0
0.020 - 0
0.200 - 0
0.080 - 0
0.220 - 0
1.4 -
0.3 -
SAMPLING (10/
5
15.3
9.6
465.
8.3
175.
.066
.027
.110
.030
.200
.180
.310
3.8
1.1
SITES
MEAN
14.2
8.0
444.
8.2
129.
0.040
0.022
0.096
0.043
0.200
0.139
0.296
2.4
0.7
17/75)
MEDIAN
14.5
7.8
446.
8.2
123.
0.037
0.024
0. 100
0.040
0.200
0. 140
0.300
2.4
0.8
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B. Biological Characteristics:
1. Phytoplankton -
Sampling
Date
05/19/75
09/02/75
10/17/75
2. Chlorophyll a^ -
Sampling
Date
05/19/75
09/02/75
10/17/75
Dominant
Genera
1. Fragilaria sp.
2. Asterionella sp.
3. Chroomonas (?) sp.
4. Centric diatoms
5. Cryptomonas sp.
Other genera
Total
1. Aphanizomenon sp.
2. Chroomonas (?) sp_.
3. Cryptomonas sp.
4. Anabaena sp.
5. Dinobryon sp.
Other genera
Total
1. Chroomonas (?) sp.
2. Nayicula sp.
3. Aphanizomenon sp.
4. Cryptomonas sp.
5. Synedra sp.
Other genera
Total
Station
Number
1
2
3
4
5
1
2
3
4
5
1
2
3
4
5
Algal Units
per ml
2,777
6,175
2,187
350
225
125
75
50
100
925
Chlorophyll a
Cm/1)
8.7
11.3
8.9
13.6
10.9
4.3
3.1
2.0
13.0
2.6
1.7
2.4
1.4
3.8
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8
C. Limiting Nutrient Study:
Due to significant changes in nutrient levels in the samples
during shipment from the field to the laboratory, the algal assay
results are not considered representative of conditions in the
reservoir at the time the samples were collected (05/19/75 and
10/17/75).
Following is a tabulation of the mean inorganic nitrogen/
orthophosphorus ratios at each of the sampling stations and times
with the indicated limiting nutrient in parentheses.
Station 05/12/75 09/02/75 10/17/75
1 11/1 (N) 10/1 (N) 7/1 (N)
2 21/1 (P) 7/1 (N) 7/1 (N)
3 13/1 (N?) 7/1 (N) 6/1 (N)
4 8/1 (N) 19/1 (P) 5/1 (N)
5 - 9/1 (N) 13/1 (N?)
Nitrogen limitation, as indicated by the algal assay or by
in-reservoir nitrogen to phosphorus ratios, does not necessarily mean
that the trophic condition of the reservoir can be improved by con-
trolling nitrogen inputs. In many cases, the apparent condition
of nitrogen limitation results from excessive phosphorus input
from point sources and is often accompanied by a corresponding
increase in primary production. In such cases, the reversal of
the enriched condition depends upon phosphorus control, not nitro-
gen control.
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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 map (page v), except for the high
runoff 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 October, 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
determined by using a modification of a U.S. Geological Survey computer
program for calculating stream loadings*. Nutrient loads shown are
those measured minus point-source loads, if any.
Nutrient loads for unsampled "minor tributaries and immediate
drainage" ("ZZ" of U.S.G.S.) were estimated using the means of the
nutrient loads, in kg/km2/year, at stations G-l and J-l and multi-
plying the means by the ZZ area in km2.
The operator of the Riverton wastewater treatment plant provided
monthly effluent samples and corresponding flow data. The operator
of the Shoshoni wastewater treatment plant also provided monthly sam-
ples, but corresponding flows were not available. Therefore, nutrient
loads for Shoshoni were estimated at 1.134 kg P and 3.401 kg N/capita/
* See Working Paper No. 175.
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10
year as were the loads for the wastewater treatment plants at Hudson
and Lander which were not sampled.
A. Waste Sources:
1. Known municipal -
Name
Ri verton*
Shoshoni*
Hudson"^
Lander
Pop.
Served
7,995
562
390
7,000
Treatment
tr. filter
stab, pond
stab, pond
stab, pond
Mean Flow
(m3/d)
5,495.1
212.7**
147.6**
2,649.5**
Receiving
Water
Wind River
Poison Creek
Little Popo
Agie River
Popo Agie River
2. Known industrial - None
* Treatment plant questionnaires.
** Flows estimated at 0.3785 m3/capita/day.
t Anonymous, 1971.
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11
B. Annual Total Phosphorus Loading - Average Year:
1. Inputs -
kg P/ % of
Source yj; total
a. Tributaries (non-point load) -
Wind River 247,630 77.4
Badwater Creek 5,685 1.8
Ditch D-l 2,910 0.9
Ditch E-l 1,000 0.3
Fivemile Creek 24,520 7.7
Muddy Creek 1,865 0.6
Wyoming Canal 2,320 0.7
Cottonwood Creek 1,700 0.5
b. Minor tributaries & immediate
drainage (non-point load) - 12,070 3.8
c. Known municipal STP's -
Riverton 9,735 3.0
Shoshoni 635 0.2
Hudson 440 0.1
Lander 7,940 2.5
d. Septic tanks - Unknown ?
e. Known industrial - None
f. Direct precipitation* - 1,570 0.5
Total 320,020 100.0
2. Outputs -
Reservoir outlet - Wind River 30,360
3. Net annual P accumulation - 289,660 kg.
* See Working Paper No. 175.
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12
C. Annual Total Nitrogen Loading - Average Year:
1. Inputs -
kg N/ % of
Source yr total
a. Tributaries (non-point load) -
Wind River 1,553,590 58.9
Badwater Creek 30,065 1.1
Ditch D-l 14,635 0.6
Ditch E-l 18,275 0.7
Fivemile Creek 486,795 18.4
Muddy Creek 23,435 0.9
Wyoming Canal 156,520 5.9
Cottonwood Creek 24,435 0.9
b. Minor tributaries & immediate
drainage (non-point load) - 168,975 6.4
c. Known municipal STP's -
Riverton 37,740 1.4
Shoshoni 1,910 0.1
Hudson 1,325 0.1
Lander 23,805 0.9
d. Septic tanks - Unknown ?
e. Known industrial - None
f. Direct precipitation* - 96.990 3.7
Total 2,638,495 100.0
2. Outputs -
Reservoir outlet - Wind River 1,277,070
3. Net annual N accumulation - 1,361,425 kg.
* See Working Paper No. 175.
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13
D. Non-point Nutrient Export by Subdrainage Area:
Tributary kg P/km2/yr kg N/km2/yr
Wind River 22 137
Badwater Creek 3 14
Fivemile Creek 23 450
Muddy Creek 2 27
Cottonwood Creek 4 57
E. Mean Nutrient Concentrations in Ungaged Streams:
Mean Total P Mean Total N
Tributary Cone, (mg/1) Cone, (mg/1)
Poison Creek 0.617 2.251
Birdseye Creek 0.037 1.611
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14
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/mVyr 3.56 3.22 29.4 15.2
Vollenweider phosphorus loadings
(g/m2/yr) based on mean depth and mean
hydraulic retention time of Boysen Reservoir:
"Dangerous" (eutrophic loading) 0.72
"Permissible" (oligotrophic loading) 0.36
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15
V. LITERATURE REVIEWED
Anonymous, 1971. Inventory of municipal waste facilities. EPA
Publ. OWP-1, vol. 8, Washington, DC.
Martin, R. 0. R., and Ronald L. Hansen, 1966. Reservoirs in the
United States. Water Supply Paper 1838, U.S. Geol. Surv.,
Wash., DC.
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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VI. APPENDICES
16
APPENDIX A
LAKE RANKINGS
-------
TO
COJt
S601
560?
bOC-
15-
£.e LAKE
5604 LAKE OE SMtT
5605 FLAMING GOSGE
5606 FREMONT L«K£
S607 GLENDO RESERVOIR
S608 K£V HOLE ^ESEKVUIR
560^ OCEAN LAKE
5610 SEMINOLE RESE>
-------
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
4
Kilograms x 2.205 = pounds
Kilograms/square.kilometer x 5,711 = Ibs/square mile
-------
E-^CE'iT UF '.iKES «IT-i
~ES£-
( 3)
( 9)
( 0)
< 9)
( 1)
( 8)
( 11)
( 4)
( 11)
( 5)
( 6)
( 2)
DOO-
M-t A'l
0
9?
?3
62
77
100
31
39
8
46
69
54
15
85
StC
( 0)
( 12)
< 3)
( o)
( 10)
< 13)
( 4)
( 5)
( 1)
( 6)
( 9)
( 7)
( 2)
( 11)
WE A'J
CrlLO"
77 (
100 (
46 (
IS (
54 (
85 (
23 (
31 (
38 (
92 (
62 (
0 <
8 (
69 (
A
10)
13)
0)
2)
7)
11)
3)
4)
5)
12)
8)
0)
1)
9)
15
MI'N
77
^2
B
69
46
100
38
15
85
54
0
27
27
62
00
i ID)
( 12)
( 1)
( 9)
( 6)
( 13)
( 5)
( 2)
< ID
( 7)
( 0)
( 3)
( 3)
( 8)
-1EOI
OISs 0-
4 l
92 <
«2 <
62 (
H5 (
100 (
42 (
69 (
77 (
54 (
31 (
0 (
15 (
23 (
! AN
-------
LAKFS RANKED BY INDE* NOS.
•RANK LAKE CODE LAKE NAME INDEX NO
1 5603 80ULUER LAKt 560
2 5606 FREMONT LAKE 558
3 5605 FLAMING GO^UE KESERVGI« 347
4 5610 SEMINOLE RESERVOIR 339
5 5609 OCEAN LAKE 336
6 5604 LAKE OE SMET 335
7 5614 YELLOWTAIL RESERVOIR 331
8 5608 KEY HOLE RESERVOIR ?e<*
9 5611 SODA LAKE ?77
10 5601 8IG SANDY RESEKVOIR 216
11 5603 BOYSEN RESERVOIR 188
12 5607 GLENDO RESERVOIR 173
13 5612 VIVA NAUGHTON RESERVOIR 134
14 5613 WOODRUFF NArJROwS RESERVO 119
-------
APPENDIX C
TRIBUTARY FLOW DATA
-------
TRIBUTARY FLOW INFORMATION FOR WYOMING
08/05/76
LAKE CODE 5603
BOYSEN RESERVOIR
TOTAL DRAINAGE AREA OF LAKE(SO KM) 19945.6
SUR-DRAINAGE
TRIBUTARY AREA(SO KM)
JAN
FEB
MAR
APR
MAY
NORMALIZED FLOWS(CMS)
JUN JUU AUG
SEP
OCT
NOV
oec
SUMMARY
TOTAL DRAINAGE AREA OF LAKE = 19945.6
SUM OF SUB-DRAINAGE AREAS = 19950.8
TOTAL FLOW IN
TOTAL FLOW OUT
548.14
MEAN MONTHLY FLOWS AND DAILY FLOWS(CMS)
TRIBUTARY MONTH YEAR MEAN FLOW DAY
5603A1
FLOW DAY
FLOW DAY
FLOW
5603A2
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
30.865
3C.299
42.192
33.131
28.883
29.166
37.945
45.307
64.562
119.780
60.881
39.077
25.485
21.521
15.574
13.309
14.158
17.556
14.725
36.812
105.622
173.299
20.530
12.176
7
4
2
2
3
1
1
3
1
1
2
7
4
1
1
16
15
1
2
34.830
28.600
29.450
56.067
29.166
29.166
22.285 15
62.297 16
65.695 15
71.925
46.156
25.485
25.485
16.990
12.459 15
147.531
207.562
55.784
11.100
33.980
66.261
158.574
29.733
MEAN
5603A1
B603A2
560381
5603D1
5603E1
5603F1
5603G1
5603H1
5603J1
5603ZZ
19P45.6
11370.1
2092.7
0.0
0.0
1082.6
859.9
0.0
427.3
4118.1
33,92
16.99
0.023
0.0
0.0
1.27
0.057
0.0
0.0
0.028
32.71
16.71
0.538
0.0
0.0
1.33
0.142
0.0
0.0
0.425
33ol2
17.84
1.076
0.0
0.0
1.42
0.396
0.0
0.0
0.057
34.21
26.33
1.161
0.0
0.0
2.01
0.453
0.0
0.028
0.198
38.40
74.76
1.982
0.0
0.142
4.47
0.736
0.142
0.227
0.566
56.18
153.48
1.784
0.113
0.142
7.48
1.076
0.283
0.085
0.425
69.32
70.51
0.481
0.085
0.142
Q.86
1.104
0.425
0.085
0.142
39.36
22.65
0.198
0.142
0.142
8.98
1.076
0.383
0.113
0.028
36.87
20.10
0.227
0.142
0.142
7.31
0.651
0.283
0.057
0.028
33.73
19.26
0.198
0.0
0.0
3.62
0.340
0.0
0.057
0.028
36.19
21.80
0.113
0.0
0.0
1.95
0.227
0.0
0.0
0.028
35.57
18.12
0.028
0.0
0.0
1.50
0.085
0.0
0.0
0.028
40.00
39.90
0.650
0.040
0.059
4.20
0.531
0.119
0.055
0.163
-------
TRIBUTARY FLOW INFORMATION FOR WYOMING
08/05/76
LAKE CODE 5603 BOYSEN RESERVOIR
MEAN MONTHLY FLOWS AND DAILY FLOWS(CMS)
TRIBUTARY MONTH YEAR MEAN FLOW DAY
S603B1
560301
5603E1
5603F1
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
FLO* DAY
FLOW DAY
FLOW
0.0
0.0
0.0
0.0
0.142
0.566
1.133
5.663
14.158
8.495
0.142
0.142
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.142
0.113
0.085
0.142
0.142
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.113
0.142
0.170
0.142
0.142
3.964
2.464
1.812
1.671
1.388
1.472
1.416
3.398
7.900
12.035
12.431
9.203
2
3
1
1
3
1
2
1
16
1
2
15
3
1
15
2
7
4
2
2
3
1
1
3
1
1
2
0.142
0.283
0.566
12.743 15
29.733 16
22.653 15
0.283
0.142
0.113
0.227
0.085
0.057
0.142
0.227
0.142
0.142
4.219
2.860
1.926
1.586
1.869
1.133
2.492 15
4.219 16
9.288 15
13.026
10.477
1.246
28.317
1.416
4.389
7.362
12.063
-------
TRIBUTARY FLOW INFORMATION FOR WYOMING
03/05/76
LAKE CODE 5603 bOYSEN RESERVOIR
MEAN MONTHLY FLOWS AND DAILY FLOWS
TRIBUTARY MONTH YEAR MEAN FLOW DAY
5603G1
5603H1
5603J1
560322
10
11
12
i
2
3
it
5
6
7
8
9
10
11
1?
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
0.453
0.396
0.170
0.170
0.255
0.425
0.595
1.586
1.699
1.812
1.699
0.878
0.0
0.0
0.0
0.0
0.0
0.0
0.0
0.142
0.283
0.425
0.283
0.283
0.057
0.057
0.057
0.057
0.057
0.057
0.057
0.142
0.113
0.085
0.057
0.057
0.028
0.028
0.028
0.028
0.283
0.142
0.425
1.133
0.850
0.283
0.142
0.142
7
4
2
3
1
1
3
1
1
2
3
1
1
7
4
2
3
1
1
3
1
1
FLOW DAY
0.340
0.425
0.510
FLOW DAY
FLOW
0.368
0.736
0.453
0.850
1.501
1.699
1.246
15
16
15
1.359
1.501
1.699
0.255
0.425
0.283
0.085
0.057
0.057
0.057
0.057
0.113
0.142
0.085
0.057
16
15
0.311
0.425
15
15
0.142
0.057
-------
APPENDIX D
PHYSICAL and CHEMICAL DATA
-------
STOrtET RETRIEVAL DATE 76/08/05
560301
43 14 30.0 108 10 45.0 3
BOYSEN RESERVOIR
56013 WYOMING
090291
11EPALES 2111202
0009 FEET DEPTH CLASS 00
DATE
FROM
TO
75/05/19
75/09/02
75/10/17
DATE
FROM
TO
75/05/19
75/09/02
75/10/17
TIMF DEPTH
OF
DAY FEET
13 30 0000
13 30 0005
11 45 0000
11 45 0005
11 45 0015
16 15 0000
16 15 0005
16 15 0015
TIME DEPTH
OF
DAY FEET
13 30 0000
13 30 0005
11 45 0000
11 45 0005
11 45 0015
16 15 0000
16 15 0005
16 15 0015
00010
WATER
TEMP
CENT
14.1
13.8
20.2
20.0
19.7
14.1
13.9
12.3
00665
PHOS-TOT
MG/L P
0.100
0.072
0.075
0.044
C.062
0.037
0.039
0.066
00300
00
MG/L
7.4
7.8
7.2
7.0
7.2
8.4
8.2
7.6
32217
CHLRPHYL
A
UG/L
8.7
10.9
2.6
00077
TRANSP
SECCHI
INCHES
8
13
26
00031
INCDT LT
REMNING
PERCENT
00094
CNDUCTVY
FIELD
MICROMHO
584
593
510
504
508
438
438
426
00400
PH
SU
8.20
8.40
8.60
8.60
8.60
8.15
8.20
8.20
00410
T ALK
CAC03
MG/L
160
164
135
135
119
133
133
145
00610
NH3-N
TOTAL
MG/L
0.100
0.080
0.020
0.020
0.040
0.020K
0.020K
0.060
00625
TOT KJEL
N
MG/L
0.600
0.500
0.600
0.400
0.400
0.200
0.200
0.200K
00630
N02&N03
N-TOTAL
MG/L
0.180
0.170
0.040
0.040
0.080
0.100
0.100
0.090
00671
PHOS-OIS
ORTHO
MG/L P
0.024
0.023
0.009
0.008
0.008
0.020
0.020
0.015
K VALUE KNOWN TO BE
LESS THAN INDICATED
-------
STORE! RETRIEVAL DATE 76/06/05
DATE
FROM
TO
75/05/19
75/09/02
75/10/17
TIME
OF
DAY
14 40
14 40
14 40
14 40
11 15
11 15
11 15
11 15
11 15
14 40
14 40
14 40
14 40
DEPTH
FEET
0000
0005
0015
0033
0000
0005
0015
0030
0052
0000
0005
0015
0045
00010
WATER
TEMP
CENT
14.2
14.2
13. 8
9.8
20.3
20.2
20. 1
19.6
19.8
14.9
14.6
14.1
13.2
560302
43 16 03.0 108 11 47.0 3
bOYSEN RESERVOIR
56013 nlYOMINU
090291
11EPALES
2111202
0037 FEET DEPTH CLASS
00300
00
MG/L
7.6
8.4
8.6
8.0
7.2
7.2
7.6
7.4
6.8
8.4
7.8
8.0
8.0
00077
TRANSP
SECCHI
INCHES
14
54
34
00094
CNDUCTVY
FIELD
MICROMHO
597
593
619
583
426
423
427
430
438
437
430
450
458
00400
PH
SU
8.50
8.50
8.40
8.50
8.65
8.70
8.65
8.60
8.60
8.20
8.20
8.20
8.25
00410
T ALK
CAC03
MG/L
165
163
175
175
118
115
118
117
116
127
129
140
142
OOblO
NH3-N
TOTAL
MG/L
0.060
0.060
0.050
0.060
0.020
0.020K
0.020
0.020
0.030
0.070
0.080
0.050
0.050
00
00625
TOT KJEL
N
MG/L
0.700
0.600
0.500
0.200
0.300
0.300
0.400
0.400
0.400
0.200
0.200
0.200
0.200
00630
N02&N03
N-TOTAL
MG/L
0.150
0.150
0.140
0.150
0.020K
0.020K
0.020
0.020
0.040
0.100
0.100
0.100
0.100
00671
PHOS-DIS
ORTHO
MG/L P
0.008
0.007
0.012
0.013
0.006
0.005
0.007
0.006
0.009
0.026
0.023
0.019
0.019
DATE
FROM
TO
75/05/19
75/09/02
75/10/17
00665 32?17 00031
TIME DEPTH PHOS-TOT CrtLRPHYL INCDT LT
OF A REMNING
DAY FEET
14
14
14
14
11
11
11
11
11
14
14
14
14
40
40
40
40
15
15
15
15
15
40
40
40
40
0000
0005
0015
0033
0000
0005
0015
0030
0052
0000
0005
0015
0045
MG/L P
0,
0,
0,
0,
0,
0,
0,
0,
0,
0,
0,
0,
0,
.050
,056
.033
.035
.021
.030
.024
.025
.068
.039
.037
.044
.047
UG/L PERCENT
11. 3
4.3
1.7
K VALUE KNOWN TO BE
LESS THAN INDICATED
-------
STORE! RETRIEVAL DATE 76/08/05
560303
43 21 22.0 108 12 49.0 3
BOYSEN RESERVOIR
56013 WYOMING
130791
DATE
FROM
TO
75/05/19
75/09/02
75/10/17
DATE
FROM
TO
75/05/19
75/09/02
75/10/17
TIME DEPTH
OF
DAY FEET
15 00 0000
15 00 0005
15 00 0017
15 00 0038
10 40 0000
10 40 0005
10 40 0015
10 40 0030
10 40 0046
17 00 0000
17 00 0005
17 00 0015
17 00 0035
17 00 0055
TIME DEPTH
OF
DAY FEET
15 00 0000
15 00 0005
15 00 0017
15 00 0038
10 40 0000
10 40 0005
10 40 0015
10 40 0030
10 40 0046
17 00 0000
17 00 0005
17 00 0015
17 00 0035
17 00 0055
00010
WATER
TEMP
CENT
8.9
8.9
8.3
7.1
19.8
19.8
19.8
19.8
18.6
15.3
14.6
14.4
14.4
14.3
00665
PHOS-TOT
MG/L P
0.031
0.024
0.023
0.028
0.023
0.019
U.017
0.018
0.038
0.037
0.038
0.034
0.034
0.038
00300 00077
00 TR4NSP
MG/L
9
9
9
8
7
7
7
7
4
7
7
8
7
8
3221
SECCHl
INCHES
.8 48
.4
.2
.8
.0 57
.0
.2
.0
.4
.6 42
.6
.2
.8
.0
7 00031
00094
CNDUCTVY
FIELD
MICROMHO
530
528
523
505
415
416
418
417
463
432
430
441
448
454
11EPALES 2111202
0043 FEET DEPTH CLASS oo
00400 00410 00610 00625 00630
PH T ALK NH3-N TOT KJEL N026.N03
SU
8.30
8.50
8.50
8.50
8.60
8.60
8.60
8.60
8.20
8.30
8.25
8.20
8.20
8.20
CAC03
MG/L
169
169
157
160
111
114
114
115
125
118
120
123
122
119
TOTAL
MG/L
0.040
0.040
0.050
0.050
0.020
0.020K
0.020K
0.020
0.020K
0.040
0.040
0.040
0.040
0.040
N N-TOTAL
MG/L
0.400
0.300
0.400
0.300
0.300
0.300
0.300
0.300
0.200
0.200K
0.200
0.200
0.200
0.200
MG/L
0.130
0.120
0.160
0.150
0.030
0.020
0.020
0.020
0.160
0.110
0.100
0.100
0.100
0.100
00671
PHOS-DIS
ORTHO
MG/L P
0.017
0.014
0.014
0.012
0.006
0.007
0.005
0.006
0.024
0.025
0.024
0.024
0.025
0.025
CHLRPHYL INCDT LT
A
OG/L
8
3
2
REMNING
PERCENT
.9
.1
.4
K VALUE KNOWN TO BE
LESS THAN INDICATED
-------
STORET RETRIEVAL DATE 76/08/05
560304
43 23 07.0 108 11
BOYSEN RESERVOIR
56013 WYOMING
15.0 3
090291
11EPALES
2111202
0050 FEET DEPTH CLASS
DATE
FROM
TO
75/05/19
75/09/02
75/10/17
DATE
FROM
TO
75/05/19
75/09/0?
75/10/1 7
TIME DEPTH
OF
DAY FEET
15 20 0000
15 ?0 0005
15 20 0020
15 20 0030
15 20 0046
10 05 0000
10 05 0005
10 05 0015
10 05 0035
10 05 0065
10 05 0098
17 20 0000
17 20 0005
17 20 0015
17 20 0040
17 20 0070
17 ?0 0094
TIME DEPTH
OF
DAY FEET
15 ?0 0000
15 20 0005
15 20 0020
15 20 0030
15 20 00^6
10 05 0000
10 05 0005
10 05 0015
10 05 0035
10 05 0065
10 05 0096
17 20 0000
17 ?0 0005
17 20 0015
17 ?0 0040
17 20 0070
17 20 0094
00010
WATER
TEMP
CENT
11.9
11.3
11.5
9.5
7.4
19.9
20.0
19.8
19.1
15.3
14.5
14.6
14.6
14.6
14.6
14.5
14.5
00665
PHOS-TOT
MG/L P
0.021
0.039
0.030
0.028
0.023
0.020
0.022
0.022
0.045
0.077
0,264
0.032
0.035
0.037
0.034
0.042
0.045
00300 00077
DO TRANSP
SECCHI
MG/L INCHES
9.4 60
9.0
11.0
11.0
10.0
6.6 60
6.4
6.8
4.0
3.4
0.6
7.8
7.6
7.6
8.2
7.8
7.7
32217 00031
CHLRPHYL INCDT LT
A PEMNING
UG/L PERCENT
13.6
2.0
1.4
00094
CNDUCTVY
FIELD
MICKOMHO
567
555
555
530
500
423
420
422
456
523
538
447
446
451
458
453
465
00400
PH
SU
8.60
8.80
8.50
8.60
8.50
8.40
8.45
8.40
8.15
7.80
7.75
8.30
8.25
8.25
8.20
8.20
8.20
00410
T ALK
CAC03
MG/L
159
164
168
166
165
112
114
114
120
145
146
121
119
123
122
121
124
00610
NH3-N
TOTAL
MG/L
0.030
0.030
0.030
0.030
0.030
0.030
0.020
0.020K
0.020K
0.020K
0.070
0.040
0.040
0.040
0.050
0.020K
0.020K
00
00625
TOT KJEL
N
MG/L
0.500
0.600
0.600
0.500
0.500
0.300
0.200
0.200
0.200
0.200
0.400
0.200
0.200K
0.200
0.200
0.200
0.200K
00630
N02&N03
N-TOTAL
MG/L
0.060
0.070
0.060
0.090
0.140
0.040
0.040
0.050
1.400
0.300
0.300
0.100
0.100
0.100
0.100
0.100
0.100
00671
PriOS-OIS
ORTHO
MG/L P
0.017
0.015
0.019
0.009
0.012
0.009
0.008
0.011
0.025
0.062
0.014
0.024
0.024
0.025
0.025
0.027
0.027
K VALUE KNOWN TO BE
-------
STORE! RETRIEVAL OAT£ 7fa/08/05
560305
*3 12 16.0 108 11 02.0 3
BOYSEN RESERVOIR
56013 WYOMING
11EPALES 760109 3111202
0008 FEET DEPTH CLASS 00
DATE
FROM
TO
75/09/02
75/10/17
DATE
FROM
TO
75/09/02
75/10/17
TIME DEPTH
OF
DAY FEET
11 55 0000
11 55 0005
16 00 0000
TIME DEPTH
OF
DAY FEET
11 55 0000
11 55 0005
16 00 0000
00010
WATER
TEMP
CENT
19.5
18.8
11.*
00665
PHOS-TOT
MG/L P
0.055
0.099
0.037
00300
DO
MG/L
7.2
6.8
9.8
32217
CHLRPHYL
A
UG/L
13.0
3.8
00077 0009* 00*00 00*10 00610 00625 00630 00671
TRANSP CNDUCTVY PH T ALK NH3-N TOT KJEL N02&N03 PHOS-OIS
SECCHI FIELD CAC03 TOTAL N N-TOTAL ORTHO
INCHES MICHOMHO SU MG/L MG/L MG/L MG/L MG/L P
1* 567 8.*0
562 8.50
13 435 8.35
00031
INCDT LT
REMNING
PERCENT
165 0.030 0.500 0.020K 0.006
166 0.020K 0.500 0.020K 0.00*
175 0.060 0.200K 0.020K 0.006
K VALUE KNOWN TO BE
LESS THAN INDICATED
-------
APPENDIX E
TRIBUTARY AND WASTEWATER
TREATMENT PLANT DATA
-------
STORET RETRIEVAL DATE 76/Ob/05
56G3A1
43 25 03.0 108 10 37.0 4
WIND RIVER
56 7.5 BOYSEN
0/tfOrSEN KESERVOIft
BELO* BOYSEN 0AM 1.3 MI
11EPALES
0000 FEET DEPTH
090391
NNW BOYSEN CAMP
2111204
LASS 00
DATE TIME DEPTH N02S.N03
FROM OF
TO DAY FEET
7W10/07
74/11/04
74/12/02
75/01/02
75/03/03
75/04/01
75/05/01
75/05/15
75/06/03
75/06/16
75/07/01
75/07/15
75/08/01
75/09/02
75/10/02
08 20
08 10
09 00
09 05
08 31
10 30
09 50
07 15
11 15
13 30
10 15
09 00
09 00
18 40
11 10
0630
'S.N03
OTAL
IO./L
0.104
1.010
0.140
0.144
0.110
0.260
0.150
0.135
0.075
0.080
0.075
0.130
0.150
0.125
0.080
00625
TOT KJEL
N
MG/L
0.400
0.900
0.600
0.600
0.450
0.450
2.300
0.700
0.500
2.000
1.700
0.400
0.400
0.600
0.600
00610
NH3-N
TOTAL
MG/L
0.045
0.050
0.075
0.048
0.040
0.040
0.085
0.077
0.040
0.060
0.070
0.035
0.020
0.015
0.060
00671
PHOS-DIS
ORTriO
MG/L P
0.020
0.025
0.015
0.015
0.015
0.005
0.010
0.005K
0.005
0.005
0.015
0.020
0.025
0.025
0.040
00665
PHOS-TOT
MG/L P
0.035
0.040
0.020
0.020
0.015
0.020
0.010K
0.010
0.020
0.020
0.030
0.030
0.040
0.060
K VALUE KNOWN TO BE
LESS THAN INDICATED
-------
STORE! RETRIEVAL DATE 76/03/05
5603A2
43 07 45.0 108 13 30.0 4
WIND RIVER
56 7.5 HIDDEN VALLY
T/BOYSEN RESERVOIR 090291
bNK END OF RD .6 MI S OF AIRSTRIP
11EPALES 2111204
0000 FEET OEPTrt CLASS 00
DATE TIME DEPTH
FROM or
TO DAY FEET
74/10/07 11 45
74/11/04 10 ?0
75/04/01 14 10
75/05/01 13 05
75/05/15 11 10
75/06/16 15 05
75/07/15 11 45
75/08/01 13 35
75/09/02 08 05
OC630
N02S.N03
N-TUTAL
MG/L
0.056
0.272
0.190
0.070
0.085
0.075
0.065
0.010
0.065
00625
TOT KJEL
N
MG/L
0.800
0.600
0.900
1.850
2.000
2.000
0.950
0.100
0.600
00610
NH3-N
TOTAL
MG/L
0.025
0.025
0.080
0.080
0.045
0.085
0.020
0.010
0.025
00671
PHOS-DIS
ORTHO
MG/L P
0.010
0.020
0.045
0.045
0.050
0.040
0.030
0.020
0.030
00665
PHOS-TOT
MG/L P
0.050
0.050
0.140
0.050K
0.500
0.400
0.310
0.040
0.080
K VALUE KNOWN TO BE
LESS THAN INDICATED
-------
STOWET RETRIEVAL OATE 76/06/05
560361
43 16 10.0 108 04 i*5.0 4
SADWATEH CREEK
56 7.5 BONNtVLLt
T/BOYSEN RESEHVOIK 090291
GAGING STATION .4 MI to OF BONNEV1LLE
11EPALES 2111204
0000 FEET DEPTH CLASS 00
OATE TIME DEPTH N02S.N03
FROM OF
TO DAY FEET
75/02/02
75/03/03
75/04/01
75/05/01
75/05/15
75/06/03
75/06/16
75/07/01
75/07/15
75/08/01
75/10/02
14
09
11
10
10
00
20
15
07 45
11 40
14 00
10 45
09 45
11 15
11 32
0630
S.N03
OTAL
G/L
0.005K
0.005
0.105
0.195
0.130
0.070
0.030
0.040
0.030
0.010
0.035
006?5
TOT KJEL
N
MG/L
0.700
1.200
0.600
2.200
3.180
1.950
4.700
0.900
0.850
0.900
1.4QO
00610
NH3-N
TOTAL
MG/L
0.017
0.025
0.045
0.040
0.030
0.020
0.050
0.025
0.020
0.020
0.030
00671
PHOS-OIS
ORTHO
MG/L P
0.008K
0.010
0.010
0.035
0.045
0.040
0.035
0.040
0.035
0.015
0.005
00665
PHOS-TOT
MG/L P
0.020
0.010
0.130
0.920
2.600
1.900
0.580
0.440
0.210
0.030
0.090
K VALUE KNOWN TO BE
LESS THAN INDICATED
-------
STORE! RETRIEVAL DATE 76/08/05
5603C1
43 14 11.0 108 08 20.0 4
POISON CREEK
56 7.5 MIDDEN YALLY
T/80YSEN RESERVOIR 090291
400 FT END DRT RD .8 MI ENEWTR TANK HILL
11EPALES 2111204
0000 FEET DEPTH CLASS 00
DATE
FROM
TO
74/11/04
75/04/01
75/05/01
75/06/03
75/06/16
75/07/01
75/07/15
75/08/01
75/09/03
75/10/02
00630 00625
TIME DEPTH N02&N03 TOT KJEL
OF N-TOTAL N
DAY FEET
08
12
11
12
14
11
10
11
07
12
55
15
55
25
40
15
45
25
20
23
MG/L
0
0
0
C
0
0
0
0
0
0
.080
.095
.040
.185
.125
. 160
.070
.010
.005
.010
MG/L
1.
4.
0.
5.
3.
1 .
1.
2.
0.
1.
300
000
600
000
150
700
880
200
700
200
00610 00671 00665
NHS-N PHOS-DIS PHOS-TOT
TOTAL ORTriO
MG/L
0.
1.
0.
0.
0.
0.
0.
0.
0.
0.
050
250
165
775
250
260
065
045
025
050
MG/L
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
P
450
313
570
400
410
550
725
620
050
025
MG/L P
0.610
0.770
0.690
0.610
0.570
0.740
0.920
0.920
0.080
0.060
-------
STORET RETRIEVAL DATE 76/03/05
560301
43 12 11.0 108 12 06.0 4
DITCH
56 7.5 HIDDEN VALLY
T/BOYSEN RESERVOIR 090291
BROG ON LOTY RD 2.5 MI NE VALLEY VIEW SK
11EPALES 2111204
0000 FEET DEPTH CLASS 00
DATE TIME DEPTH N02&.N03
FROM OF
TO DAY FEET
75/05/01 12 45
75/06/16 15 30
75/08/01 15 15
75/09/02 07 45
0630
'&.N03
OTAL
IG/L
0.015
0.010
0.210
0.005
00625
TOT KJEL
N
MG/L
0.900
0.900
0.150
0.200
00610
NH3-N
TOTAL
MG/L
0.015
0.040
0.020
0.005K
00671
PHOS-DIS
ORTHO
MG/L P
0.010
0.015
0.020
0.010
00665
PHOS-TOT
MG/L P
0.060
0.070
0.070
0.040
K VALUE KNOWN TO BE
LESS THAN INDICATED
-------
STO^ET RETRIEVAL DATE 76/06/05
DATE TIME DEPTH N02S.N03
FROM OF
TO DAY FEET
75/03/02
75/05/15
75/06/03
75/07/01
75/07/15
75/09/02
75/10/0?
15
11
12
11
11
08
12
15
30
35
?5
00
30
35
5603E1
43 13 21.0 108 12 26.0 4
OITCri
56 7.5 HIDDEN VALLY
T/80YSEN RESERVOIR 090291
BRDG ON DIRT »D 3.1 MI N£ VLY VIEW STORE
11EPALES 3111204
0000 FEET DEPTH CLASS 00
0630
'S.N03
OTAL
IG/L
3.765
0.005
0.005
0.005
0.010
0.005
0.010
00625
TOT KJEL
N
MG/L
1.300
0.950
0.250
1.200
0.450
0.800
0.700
00610
NH3-N
TOTAL
MG/L
0.068
0.020
0.005
0.025
0.020
0.025
0.015
00671
PHOS-DIS
ORTHO
MG/L P
0.012
0.010
0.005K
0.025
0.035
0.020
0.005K
00665
PHOS-TOT
MG/L P
0.040
0.060
0.040
0.050
0.105
0.065
0.020
K VALUE KNOWN TO BE
LESS THAN INDICATED
-------
STORET RETRIEVAL DATE 76/06/05
5603F1
43 13 21.0 108 13 07.0 4
FIVEMILE CREEK
56 7.5 MIDDEN VALLY
T/80Y5EN RESERVOIR 090291
BROG ON LOTY RD .4 MI Nw JCT * US 26
11EPALES 2111204
0000 FEET DEPTH CLASS 00
DATE
FROM
TO
74/10/07
74/11/04
74/12/02
75/01/02
75/03/03
75/04/01
75/05/01
75/05/15
75/06/03
75/06/16
75/07/01
75/07/15
75/08/01
75/09/02
75/10/02
00630 00625
TIME DEPTH N02&N03 TOT KJEL
OF N-TOTAL N
DAY FEET
12
10
11
10
10
12
11
10
13
15
11
14
13
08
12
15
40
10
00
00
35
15
45
55
40
39
00
45
40
40
MG/L
1.
2.
3.
3.
3.
3.
1.
1.
0.
0.
0.
0.
0.
0.
0.
680
240
110
400
150
700
780
050
740
710
630
530
600
660
970
MG/L
1.
1.
1.
1.
2.
1.
0.
0.
0.
4.
8.
1.
0.
0.
1.
200
350
100
100
700
650
900
900
450
400
800
300
850
700
500
00610 OC671 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
0
.020
.025
.030
.056
.095
.070
.039
.070
.015
.065
.120
.040
.020
.015
.030
MG/L
0.
G.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
P
005
010
005K
005
025
012
028
010
025
165
065
085
075
030
010
MG/L P
0.035
0.025
0.020
0.020
0.110
0.060
0.200
0.240
0.080
0.500
0.330
0.250
0.210
0.110
0.070
K VALUE KNOWN TO BE
LESS THAN INDICATED
-------
STORET RETRIEVAL DATE 76/08/05
DATE TIME DEPTH N02J.N03
FROM OF
TO DAY FEET
74/10/07
74/11/04
74/12/02
75/03/03
75/04/01
75/05/01
75/05/15
75/06/03
75/06/16
75/07/01
75/07/15
75/08/01
75/09/02
75/10/02
12 50
10 50
11 30
10 20
13 00
11 31
10 20
12 55
IS 55
11 50
13 00
14 00
08 55
13 05
5603G1
43 17 10.0 108 16 30.0 4
MUDDY CREEK
56 7.5 MEX. PASS SE
T/80YSEN RESERVOIR 090291
GAGING STATN 1.5 MI SW OF LK CAMEAHrfAIT
11EPALES 2111204
0000 FEET DEPTH CLASS 00
0630
S.N03
OTAL
G/L
0.504
0.552
0.940
0.410
0.410
0.270
0.050
0.010
0.270
0.215
0.400
0.400
0.230
0.250
00625
TOT KJEL
N
MG/L
1.000
0.400
1.100
0.900
1.150
0.800
i.eoo
0.500
2.800
0.800
1.050
1.050
0.400
1.500
00610
NH3-N
TOTAL
MG/L
0.050
0.020
0.045
0.030
0.165
0.020
0.060
0.010
0.035
0.030
0.030
0.020
0.010
0.020
00671
PHOS-DIS
ORTHO
MG/L P
0.005K
0.010
0.005K
0.015
0.005K
0.010
0.02S
0.010
0.090
0.035
0.025
0.040
0.010
0.010
00665
PHOS-TOT
MG/L P
0.015
0.010
0.010
0.040
0.020
0.500
0.125
0.460
0.370
0.330
0.300
0.130
0.440
K VALUE KNOWN TO BE
LESS THAN INDICATED
-------
STORET RETRIEVAL DATE 76/08/05
5603rtl
43 16 55.0 108 12 03.0 4
^YOKING CANAL
b6 7.5 S* 60NMEVLLE
T/BOYSEN RESERVOIR 090391
30 FT FRM DRT RD 1.8 MI ME L«. CAMEAM*AIT
11EPALES 3111304
0000 FEET DEPTH CLASS 00
DATE
FKOM
TO
75/03/02
75/05/15
75/06/03
75/06/16
75/07/01
75/07/15
75/08/01
75/10/03
00630 00635
TIME DEPTH N036.N03 TOT KJEL
OF N-TOTAL N
DAY FEET
13
09
13
16
13
09
14
13
45
30
10
10
09
30
15
35
MG/L
0
0
0
0
0
0
0
c
.135
.010
.010
.030
.010
.470
.015
.010
MG/L
0.
1.
0.
1.
2.
0.
0.
0.
600
150
300
000
100
300
450
600
00610 00671 00665
NHS-N PHOS-DIS PHOS-TOT
TOTAL ORTHO
MG/L
0.
0.
0.
0.
0.
0.
0.
0.
C33
060
005
035
035
035
010
010
MG/L
0.
0.
0.
0.
0.
0.
0.
0.
p
008K
015
015
045
040
005
015
005K
MG/L P
0.030
0.060
0.370
0.140
0.030
0.070
0.030
K VALUE KNOWN TO BE
LESS THAN INDICATED
-------
STOrtET RETRIEVAL DATE 76/08/05
3603J1
43 21 15.0 108 17 05.0 4
COTTONWOOO CREEK
56 7.5 SE MtX. PASS
T/eOrSEN RESERVOIR 090291
SEC RD BRDG 1.8 Ml w OF BOrSEN RES
11EPALES 2111204
0000 FEET DEPTH CLASS 00
DATE TIME DEPTH N02S.N03
FROM OF"
TO DAY FF.ET
74/10/07
74/11/04
74/12/02
75/03/03
75/04/01
75/05/01
75/05/15
75/06/03
75/06/07
75/07/01
75/07/15
75/08/01
13
11
12
10
13
11
10
13
10
12
13
14
30
15
?5
45
30
45
00
30
?0
30
30
45
0630
'S.N03
OTAL
IG/L
C.990
0.570
0.311
1.400
0.490
C.I 90
0.135
C.005
0.045
0.005
0.100
0.125
00625
TOT KJEL
N
MG/L
1.250
1.800
0.700
1.600
0.650
0.700
1.450
1.000
0.050K
1.350
0.850
0.450
00610
NH3-N
TOTAL
MG/L
0.095
0.020
0.037
0.080
0.095
0.020
0.080
0.010
0.015
0.045
0.020
0.015
00671
PHOS-OIS
ORTHO
MG/L P
0.005K
0.015
0.005K
0.030
0.010
C.005K
0.010
0.005
0.020
0.015
0.005
0.005K
00665
PHOS-TOT
MG/L P
0.025
0.010K
0.180
0.130
0.010K
0.180
0.180
0.020
0.370
0.130
0.065
K VALUE KNOWN TO Bt
LESS THAN INDICATED
-------
STORE! RETRIEVAL DATE 7b/Cd/05
5603L1
43 22 28.0 108 07 40.0 4
BIRDSEYE CREEK
56 . 7.5 BONNEV1LE SW
T/60YSEN RESErfVOH
AT US H*Y 20 BKDG 3.3 MI
090291
SE BOYSEN 0AM
DATE TIME DEPTH
FROM OF
TO DAY FEET
75/05/15 07 30
75/06/03 11 30
75/06/16 13 35
75/07/01 10 30
00630
N02&N03
N-TOTAL
MG/L
0.220
0.010
0.010
0.005
00625
TOT KJEL
N
MG/L
1.750
0.750
2.300
1.400
00610
NH3-N
TOTAL
MG/L
0.065
0.015
0.025
0.020
00671
PHOS-niS
ORTHO
MG/L P
0.005
0.005
0.005
11EPALES
0000 FEET
00665
PHOS-TOT
MG/L P
0.050
0.030
0.030
DtPTh
2111204
CLASS 00
-------
STORET RETRIEVAL DATE 76/0^/05
5603AA TF5603AA P007995
43 01 00.0 108 21 00.0 4
RIVERTON
56 7.5 RIVERTON E.
T/aOYSEN RES. 0902*1
WIND RIVER
11EPALES 2141204
0000 FEET DEPTH CLASS 00
DATE
FROM
TO
75/02/06
CPIT1-
75/02/06
75/03/03
CP-
75/04/25
75/05/15
CP(T)-
75/05/15
75/06/04
CP(T)-
75/06/0^.
75/06/25
CP(T)-
75/06/25
75/07/17
CP(T)-
75/07/17
75/08/06
CP(T)-
75/08/06
75/08/20
CP(T)-
75/08/20
75/09/17
CP-
75/10/04
00630 00625
TIME DEPTH N02&N03 TOT KJEL
OF N-TOTAL N
DAY FEET MG/L MG/L
08
16
08
16
00
08
08
16
08
14
00
03
08
15
08
15
08
15
08
15
08
15
08
15
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
0
0
0
0
0
0
0
0
c
0
0
0
.200
.030
.151
.100
.050
.100
.050
.575
.650
.875
.325
.625
8.700
22.000
31.000
33.000
27.000
18.000
16.000
14.500
13.500
14.500
16.000
17.500
00610 00671 00665 50051 50053
NH3-N PHOS-DIS PHOS-TOT FLOW CONDUIT
TOTAL ORTrtO *ATE FLOW-MOD
MG/L MG/L P MG/L P INST MGD MONTHLY
5.
7.
9.
11.
13.
5.
0.
0.
0.
0.
0.
2.
800
900
500
000
000
300
031
975
710
240
840
100
3.800
4.500
5. 100
5.800
5.200
3.800
2.600
2.500
2.630
2.750
3.200
4.100
5.900
8.000
7.500
6.500
5.700
3.800
3.600
3. BOO
3.550
3.650
4.100
1.800
1.400
1.200
1.300
1.400
1.700
1.700
1.750
1.790
1.780
1.540
1.390
1.400
1.300
1.300
1.300
1.200
1.300
1.500
1.680
1.640
1.700
1.600
1.500
-------
STORET RETRIEVAL DATE 76/08/05
DATE TIME DEPTH >-j02*.N03
FROM or
TO DAY FEET
75/02/19
75/03/27
75/05/01
75/05/29
75/09/23
75/10/15
75/10/29
75/11/19
76/01/12
10 00
10 00
13 30
OS 00
09 30
09 00
08 30
16 00
10 00
5603CA PD5603CA POOOS62
43 13 40.0 108 07 00.0 4
SHQSHONI
56 7.5 SHOSHONI
T/BOYSEN RtS. 090291
POISON CREEK
11EPALES 2141204
0000 FEET OEPTrt CLASS 00
0630
'S.N03
OTAL
IG/L
0.080
0.029
0.050
0.050
0.025
0.075
0.050
0.065
0.027
00625
TOT KJEL
N
MG/L
15.000
17.000
13.500
24.000
16.500
37.000
14.000
17.500
21.000
00610
NH3-N
TOTAL
MG/L
S.100
3.310
0.250
0.570
0.225
0.910
0.990
0.168
5.340
00671
PHOS-OIS
ORTHO
MG/L P
3.950
4.680
4.100
5.100
5.400
7.300
6.600
6.200
4.300
00665
PHOS-TOT
MG/L P
4.500
5.700
4.200
7.300
6.900
7.300
8.100
7.700
4.800
50051
FLOW
RATE
INST MGD
0.007
0.070
50053
CONDUIT
FLOW-MGO
MONTHLY
0.007
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