U.S. ENVIRONMENTAL PROTECTION AGENCY
NATIONAL EUTROPHICATION SURVEY
WORKING PAPER SERIES
REPORT
ON
PINEVIEW ESERVOIR
WEBER COUNTY
UTAH
EPA REGION VI11
WORKING PAPER No, 853
CORVALLIS ENVIRONMENTAL RESEARCH LABORATORY - CORVALLIS, OREGON
and
ENVIRONMENTAL MONITORING & SUPPORT LABORATORY - LAS VEGAS, NEVADA
-------
REPORT
ON
PINEVIEW ESEWOIR
WEBER COUNTY
UTAH
EPAEGIONVIII
WORKING PAPER No, 853
WITH THE COOPERATION OF THE
UTAH STATE DIVISION OF HEALTH
AND THE
UTAH NATIONAL GUARD
OCTOBER, .1977
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1
CONTENTS
Page
Foreward 11
List of Utah Study Lakes and Reservoirs 1v
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 ' 13
VI. Appendices 14
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11
FOREWORD
The National Eutrophication Survey was Initiated in 1972 1n
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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111
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
fresh water 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.
ACKNOWLEDGEMENT
The staff of the National Eutrophication Survey (Office of
Research and Development, U.S. Environmental Protection Agency)
expresses sincere appreciation to the Utah Department of Social
Services and the Utah Department of Natural Resources for pro-
fessional involvement, to the Utah National Guard for conducting
the tributary sampling phase of the Survey, and to those Utah
wastewater treatment plant operators who voluntarily provided
effluent samples and flow data.
The staffs of the Bureau of Water Quality of the Division
of Health and the Division of Wildlife Resources provided inval-
uable lake documentation and counsel during the Survey, reviewed
the preliminary reports, and provided critiques most useful in
the preparation of this Working Paper series.
Major General Maurice L. Watts, the'Adjutant General of Utah,
and Project Officer Lt. Colonel T. Ray Kingston, who directed the
volunteer efforts of the Utah National Guardsmen, are also grate-
fully acknowledged for their assistance to the Survey.
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iv
NATIONAL EUTROPHICATION SURVEY
STUDY LAKES AND RESERVOIRS
STATE OF UTAH
NAME_
Bear
Deer Creek
Echo
F1sh
Flaming Gorge
Huntington
Joes Valley
Lower Bowns
Lynn
Minersville
Moon
Navajo
Newcastle
Otter Creek
Panguich
Pelican
Pineview
Piute
Porcupine
Powell
Pruess
Sevier Bridge
Starvation
Steinaker
Tropic
Utah
Willard Bay
COUNTY
Rich, UT; Bear Lake, ID
Wasatch
Summi t
Sevier
Daggett, UT;
Sweetwater, WY
Emery
Emery
Garfield
Box Elder
Beaver
Duchesne
Kane
Iron
Piute
Garfield
Uintah
Weber
Ptute
Cache
Garfteld, Kane, San
Juan, UT; Coconino, AZ
Mil lard
Ouab, Sanpete
Duchesne
Uintah
Garfteld
Utah
Box Elder
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PINEVIEW
RESERVOIR
PINEVIEW RESERVOIR
® Tributary Sampling Site
X Lake Sampling Site
^) Drainage Area Boundary
9 5 10 Km.
1 i
o Scale 5 Mi-
Ma p Location
41"10—
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PINEVIEW RESERVOIR
STORE! NO. 4916
I. CONCLUSIONS
A. Trophic Condition:
Survey data indicate that PineView Reservoir is eutrophic.
It ranked sixteenth in overall trophic quality among the 27 Utah
lakes and reservoirs sampled in 1975 when compared using a com-
bination of six parameters*. Thirteen of the water bodies had
less median total phosphorus, ten had less and three had the same
median orthophosphorus, 22 had less median inorganic nitrogen,
11 had less mean chlorophyll a^., and 16 had greater mean Secchi
disc transparency. Depression of dissolved oxygen with depth
occurred at all four sampling stations in August and at station
1 in September.
Survey limnologists noted floating macrophytes, particularly
in the North Fork arm near station 4 (see map, page v).
B. Rate-Limiting Nutrient:
The algal assay results indicate Pineview Reservoir was phos-
phorus limited at the time the sample was collected (09/23/75).
The reservoir data indicate phosphorus limitation at all sam-
pling times.
C. Nutrient Controllability:
1. Point sources—No known wastewater treatment plants
impacted the reservoir during the sampling year. Septic tanks
* See Appendix A.
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2
accounted for an estimated 0.3% of the total phosphorus input to
Pineview Reservoir during the sampling year, but a shoreline
survey would have to be done to determine the significance of
those sources.
The present phosphorus loading of 0.72 g/m2/year is a little
less than that proposed by Vollenweider (Vollenweider and Dillon,
1974) as a eutrophic loading (see page 12). However, this
loading estimate probably is too low since there was an apparent
phosphorus loss during the sampling year. Also, 25% of the inflow
(1.558 m3/sec) is ground water (Cruff, 1976), and the phosphorus
contribution of this source had to be estimated.
Because the reservoir is phosphorus limited, inputs should
be minimized to the greatest practicable extent to reduce the
present rate of eutrophication.
2. Non-point sources—Non-point sources accounted for 99.7%
of the total phosphorus load during the sampling year. The North
and South branches of the South Fork Ogden River contributed 34.5%,
the North Fork Ogden River contributed 10.4%, and four other gaged
tributaries collectively contributed 16.9%. Ground water was esti-
mated to have accounted for 26.5% of the total, and the ungaged
minor tributaries and immediate drainage contributed an estimated
9 0%
7 . \J 10 .
Survey limnologists noted that much of the land use around
the reservoir and in the drainage basin is agricultural, and
-------
3
nutrients in runoff may contribute to the eutrophicatlon of the
reservoir. Further study is needed to determine the contribution
and controllability of nutrients from this source.
-------
II. RESERVOIR AND DRAINAGE BASIN CHARACTERISTICS1
A. Morphometry :
1. Surface area: 10.12 kilometers2.
2. Mean depth: 13.4 meters.
3. Maximum depth: 24.7 meters.
4. Volume: 135.684 x 106 m3.
5. Mean hydraulic retention time: 248 days.
B. Tributary and Outlet:
(See Appendix C for flow data)
1. Tributaries -
Name
North & South Br., S. Fk.
Ogden River
Middle Fk. Ogden River
Gersten Creek
N. Fk. Ogden River
Spring Creek
Unnamed Canal H-l
Ground water
Minor tributaries &
immediate drainage - 69.9
Totals 792.8
2. Outlet -
Ogden River 802.9***
C. Precipitation****:
1. Year of sampling: 78.5 centimeters.
2. Mean annual: 51.1 centimeters.
Drainage
area (km2)*
440.3
85.5
17.1
160.6
19.4
-
-
Mean flow
(mVsec)*
2.200
0.589
0.130
1.000
0.270
0.066
1 . 558**
0.530
6.343
6.320
t Table of metric conversions—Appendix B.
tt Sudweeks, 1975; maximum depth from Ikner (1975).
* For limits of accuracy, see Working Paper No. 175, "...Survey Methods,
1973-1976".
** Cruff, 1976.
*** Includes area of reservoir.
**** See Working Paper No. 175.
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5
III. WATER QUALITY SUMMARY
Pineview Reservoir was sampled three times during the open-water
season of 1975 by means of a pontoon-equipped Huey helicopter. Each
time, samples for physical and chemical parameters were collected
from a number of depths at four stations on the reservoir (see map,
page v). During each visit, a single depth-integrated (4.6 m 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 a_ analysis. The maximum depths
sampled were 20.7 meters at station 1, 12.5 meters at station 2,
16.8 meters at station 3, and 12.2 meters at station 4.
The sampling results are presented in full in Appendix D and
are summarized in the following table.
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PARAMETER
TEMP (C)
OISS OXY
0.039
0.518
0.405
0.884
9.0
0.8
14/75)
MEDIAN
8.3
9.6
160.
8.4
105.
0.051
0.009
0.360
0.040
0.500
0.390
0.860
7.8
0.7
>E*ICAL CHARACTERISTICS rO-<
STOKET CuOE 4916
2(ML> SAMPLING < d/
ri
11.1
0.6
153.
7.8
95.
0.017
0.003
0.030
0.040
0.400
0.130
0.430
2.5
1.8
U
ANGE
- 23.8
7.2
- 237.
8.9
- 113.
- 0.043
- 0.018
- 0.460
- 0.410
- 0.700
- 0.680
- 0.960
4.5
2.6
SITES
MEAN
18.7
4.3
198.
8.3
106.
0.026
0.007
0.233
0.147
0.519
0.380
0.752
3.7
2.3
PlNEvIEw RESERVOI*
7/75)
MEDIAN
21.1
3.8
207.
8.1
110.
0.024
0.006
0.180
0.100
0.500
0.430
0.600
3.8
2.4
3RD
RANt>£
17.0 -
0.4 -
197. -
7.5 -
124. -
0.018 - 0
0.002 - 0
0.030 - 0
0.020 - 0
0.200 - 0
0.050 - 0
0.230 - 0
2.7 -
1.2 -
SAMPLING (
4
18.6
7.9
223.
8.2
134.
.090
.014
.090
.160
.500
.220
.590
7.3
2.4
SITES
MEAN
18.3
5.8
216.
8.0
130.
0.034
0.006
0.047
0.037
0.300
0.084
0.347
4.4
1.9
9/23/75)
MEDIAN
18.5
6.2
217.
8.1
130.
0.026
0.004
0.040
0.020
0.300
0.060
0.340
3.7
2.0
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B. Biological Characteristics:
1. Phytoplankton -
Sampli ng
Date
05/14/75
08/07/75
09/23/75
2. Chlorophyll <± -
Sampli ng
Date
05/14/75
08/07/75
09/23/75
Dominant
Genera
1. Chroomonas sp.
2. Cryptomonas sp.
3. Chlamydomqnas sp.
4. Schroederia sp.
5. Flagellates
Other genera
Total
1. Fragilaria sp.
2. Cryptomonas sp_.
3. Chroomonas sp.
4. Cysts
5. Schroederia sp.
Other genera
Total
1. Fragilaria sp.
2. Apham'zomenon sp.
3. Chroomonas sp.
4. Cryptomonas sp.
5. Stephanodiscus sp.
Total
Station
Number
1
2
3
4
1
2
3
• 4
1
2
3
4
Algal Units
per ml
2,552
1,411
489
326
217
217
5,212
681
306
211
118
118
69
1,503
332
166
166
165
41
870
Chlorophyll
(yg/1)
15.6
7.0
5.0
8.5
2.5
4.1
4.5
3.6
2.7
3.2
4.3
7.3
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8
C. Limiting Nutrient Study:
1. Autoclaved, filtered, and nutrient spiked -
Ortho P Inorganic N Maximum yield
Spike (mg/1) Cone, (mg/1) Cone, (mg/1) (mg/1-dry wt.)
Control 0.005 0.163 0.2
0.050 P 0.055 0.163 6.3
0.050 P + 1.0 N 0.055 1.163 18.7
1.0 N 0.005 1.163 0.2
2. Discussion -
The control yield of the assay alga, Selenastrum capri-
cornutum, indicates that the potential primary productivity
of Pineview Reservoir was moderate at the time the sample was
collected (09/23/75). 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 no greater than that
of the control.
The reservoir data also indicate phosphorus limitation.
The mean inorganic nitrogen/orthophosphorus ratios were 17/1
or greater at all sampling times, and phosphorus limitation
would be expected.
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IV. NUTRIENT LOADINGS
(See Appendix E for data)
For the determination of nutrient loadings, the Utah National
Guard collected monthly near-surface grab samples from each of the
tributary sites indicated on the map (page v). Sampling was begun
in November, 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 Utah District Office of the U.S. Geological Survey for the
tributary sites nearest the reservoir.
In this report, nutrient loads for sampled tributaries were
calculated using mean annual concentrations and mean annual flows.
Nutrient loads for unsampled ground water and "minor tributaries
and immediate drainage" ("ZZ" of U.S.G.S.) were estimated using the
mean concentrations in the eight sampled tributaries and the mean
annual ground-water and ZZ flows.
No known wastewater treatment plants impacted the reservoir
during the sampling year.
A. Waste Sources:
1. Known municipal - None
2. Known industrial - None
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10
B. Annual Total Phosphorus Loading - Average Year:
1. Inputs -
kg P/ % of
Source yr total
a. Tributaries (non-point load) -
N. & S. Br., S. Fk. Ogden
River 2,500 34.5
Middle Fk. Ogden River 370 5.1
Gertsen Creek 310 4.3
N. Fk. Ogden River 755 10.4
Spring Creek 475 6.6
Unnamed Canal H-l 65 0.9
Ground water 1,915 26.5
b. Minor tributaries & immediate
drainage (non-point load) - 650 9.0
c. Known municipal STP's - None
d. Septic tanks* - 25 0.3
e. Known industrial - None
f. Direct precipitation** - 175 2.4
Total 7,240 100.0
2. Outputs -
Reservoir outlet - Ogden River 7,775
3. Net annual P loss - 535 kg.
* Estimate based on 50 shoreline dwellings; see Working Paper No. 175.
** See Working Paper No. 175.
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11
C. Annual Total Nitrogen Loading - Average Year:
1. Inputs -
kg N/ % of
Source y_r total
a. Tributaries (non-point load) -
N. & S. Br., S. Fk. Ogden
River 67,785 31.5
Middle Fk. Ogden River 12,075 5.6
Gertsen Creek 3,675 1.7
N. Fk. Ogden River 39,200 18.2
Spring Creek 12,490 5.8
Unnamed Canal H-l 2,180 1.0
Ground water 49,230 22.9
b. Minor tributaries & immediate
drainage (non-point load) - 16,750 7.8
c. Known municipal STP's - None
d. Septic tanks* - 855 0.4
e. Known industrial - None
f. Direct precipitation** - 10.925 5.1
Total 215,165 100.0
2. Outputs -
Reservoir outlet - Ogden River 189,145
3. Net annual N accumulation - 26,020 kg.
D. Non-point Nutrient Export by Subdrainage Area:
Tributary kg P/km2/yr kg N/km2/yr
N. & S. Br., S. Fk. Ogden River 6 154
Middle Fork Ogden River 4 141
Gertsen Creek 18 215
N. Fk. Ogden River 5 244
Spring Creek 24 644
* Estimate based on 50 shoreline dwellings; see Working Paper No. 175.
** See Working Paper No. 175.
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12
E. 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 thejreceiving 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 0.72 loss* 21.3 2.6
Vollenweider phosphorus loadings
(g/m2/yr) based on mean depth and mean
hydraulic retention time of Pineview Reservoir:
"Dangerous" (eutrophic loading) 0.84
"Permissible" (oligotrophic loading) 0.42
* There was an apparent loss of phosphorus during the sampling year. This
may have been due to resolubilization of previously sedimented phosphorus,
underestimation of the ground-water phosphorus contribution, or unsam-
pled point sources discharging directly to the lake.
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13
LITERATURE REVIEWED
Cruff, Russell, 1976. Personal comnunication (hydrological budget).
U.S. Geol. Surv., Salt Lake City.
Ikner, James, 1975. Personal communication (reservoir morphometry).
U.S. Geol. Surv., Salt Lake City.
Sudweeks, Calvin K., 1975. Personal communication (reservoir mor-
phometry). UT Bur. of Env. Health, Salt Lake City.
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
14
APPENDIX A
LAKE RANKINGS
-------
uATA TO BE USED I1*
CuOE
040^ LAKE POWELL
4901 BEAK LAKE
4902 LOWER BOWN'S RESERVOIR
49U3 DEER CREEK RESERVOIR
4904 ECHO RESERVOIR
4905 LYNN RESERVOIR
4906 FISH LAKE
4907 HUNTINGTON NORTH RESERVO
4908 JOE'S VALLEY RESERVOIR
4909 MINERSVILLE RESERVOIR
4910 MOON LAKE
4911 NAVAJO LAKE
49U NEWCASTLE RESERVOIR
4913 OTTER CREEK RESERVOIR
4914 PAN8UITCH LAKE
4915 PELICAN LAKE
4916 PINEVIEW RESERVOIR
4917 PIUTE RESERVOIR
4918 PORCUPINE RESERVOIR
4919 PRUESS RESERVOIR (GARRIS
4920 SEVIER BRIDGE RESERVOIR
4921 STARVATION RESERVOIR
4922 STEINAKER RESERVOIR
4923 TROPIC RESERVOIR
4924 UTAH LAKE
4925 WILLARO BAY RESERVOIR
5605 FLAMING GORGE RESERVOI*'
MEOUN
TOTAL P
0.010
0.011
0.031
0.038
0.047
0,121
0.023
0.013
0.012
0.192
0.008
0.016
0.051
0.067
0.071
0.044
0.028
0.047
0.025
0.057
0.026
0.016
0.011
C.021
C.132
0.044
0.011
MEDIAN
INO^G N
0.410
0.040
0.040
0.215
0.170
0.200
0.040
0.040
0.045
0.060
0.040
0.040
0.040
0.040
0.040
0.050
0.300
0.150
0.110
0.140
0.355
0.040
0.040
0.050
0.320
0.060
0.690
500-
MEAN SEC
339.630
253.167
336.000
430.333
450.333
417.667
152.000
392.000
400.000
445.000
381.000
368.000
428.667
453.667
426.500
438.500
435.083
482.625
440.000
491.000
449.778
394.583
316.750
425.000
490.583
457.182
285*636
MEAN
CHL09A
3.081
0.945
5.567
9.078
6.967
3*. 600
12.483
1.900
2.483
33.583
2.700
2.000
12.467
11.767
45.950
6.350
5.692
25.329
7.860
4.533
18.222
5.675
1.844
7.200
72.012
7.567
2.500
15-
MJN 00
n.doo
9.200
9.400
14.800
14.000
10.400
10.409
7.600
11.200
8.600
9.600
6.000
13.600
10.600
14.200
8.400
14.600
11.600
12.400
8. BOO
12.400
13.200
12.600
8.400
11.400
11.000
10.400
"EOiaN
MSS OnT-'G
O.OC7
0.003
0.006
0.006
0.012
0.052
0.004
0.005
0.003
0.107
o.ooa
0.003
0.009
0.033
0.010
0.004
0.006
0.007
0.011
0.008
0.008
0.004
0.005
0.006
0.012
0.009
' 0.003-
-------
Of LAKES
LAKE
COOE LAKE NAME
HIGHER VALUES (NUMBER OF LAKES «!TH HIGHER VALUES)
o<*08 LAKE POUELL
4901 3EAR LAKE
•*902 LOMER BONN'S RESERVOIR
4903 DEER CREEK RESERVOIR
4904 ECHO RESERVOIR
4905 LYNN RESERVOIR
4906 FISH LAKE
4907 HUNTINGTON NORTH RESERVO
4908 JOE'S VALLEY RESERVOIR
4909 MINERSVILLE RESERVOIR
4910 MOON LAKE
4911 NAVAJO LAKE
4912 NEWCASTLE RESERVOIR
4913 OTTER CREEK RESERVOIR
4914 PANftUITCH LAKE
4915 PELICAN LAKE
4916 PINEVIEW RESERVOIR
4917 PIUTE RESERVOIR
4918 PORCUPINE RESERVOIR
4919 PRUESS RESERVOIR (GARRIS
4930 SEVIER BRIDGE RESERVOIR
4921 STARVATION RESERVOIR
4922 STEINAKER RESERVOIR
4923 TROPIC RESERVOIR
4934 UTAH LAKE
4925 XILLARO BAY RESERVOIR
MEDIAN
TOTAL P
96 <
90 <
46 <
42 «
31 «
8 (
62 (
77 (
81 (
0 (
100 <
69 <
23 <
15 (
12 (
37 (
50 «
27 (
58 (
19 <
54 (
73 (
as <
65 <
4 (
37 <
90 <
25>
23)
1?)
11)
8!
2)
16)
20)
21)
0)
26)
18)
6)
4)
3)
9)
13)
7)
15)
5)
1«>
19)
22)
17)
1)
9)
23)
MEDIAN
INO^VJ N
4 <
87 (
87 (
19 <
27 (
23 <
65 <
65 (
58 <
44 <
87 (
87 <
87 (
87 (
65 <
54 (
15 <
31 (
38 <
35 (
8 (
87 (
87 (
50 (
12 <
44 (
0 (
D
19)
19)
5)
7)
6)
16)
16)
15)
11)
19)
19)
19)
19)
16)
14)
4)
8)
10)
9)
2)
19)
19)
13)
3)
ID
o>
500-
M£a\ SEC
81
•Jfe
85
42
19
58
100
69
62
27
73
77
46
15
50
35
38
8
31
0
23
65
88
54
4
12
92
( 2$)
< 2S)
( 22)
( 11)
( b)
< 15)
( 26)
( 18)
( 16)
( 7)
( 19)
C 20)
( 12)
< 4)
< 13)
( 9)
; 10)
< 2)
( 8>
( 0)
( 6)
< 17)
( 23)
( 14)
< 1)
< 3)
( 24)
MEAN
CHLO^A
73 (
100 (
6b (
35 (
SO <
8 (
23 (
92 (
85 (
12 (
77 (
88 (
27 (
31 (
4 (
54 (
58 (
15 (
38 t
69 (
19 (
62 (
96 (
46 (
0 (
42 <
81 (
19)
26)
17)
9)
13)
2)
6)
24!
22)
3)
20)
23)
7)
8)
1)
14)
15)
4)
10)
18)
5)
16)
25)
12)
0)
1U
21)
15-
MIN 00
15 <
77 {
73 (
0 (
12 «
62 (
62 (
96 <
46 «
85 (
69 (
100 (
19 (
54 (
8 (
90 (
4 <
38 (
33 (
81 (
33 (
23 (
27 (
90 <
42 (
50 <
62 (
4)
20)
19)
0)
3)
15)
15)
25)
125
22)
18)
26)
5)
14)
2)
23)
1)
10)
8)
21)
8)
6)
7)
23)
ID
13)
15)
i"t
OISS
42
90
50
58
13
4
79
69
96
0
100
85
27
8
23
73
58
46
19
37
37
79
65
58
13
31
90
:UlAf<
OWT-'J f>
( ID
< c3t
( 1J)
( !•»)
( 3)
( I)
< 20)
( 18)
( 25)
< 0)
( 26)
( 22)
( 7)
( 2)
( 6)
( 19)
( 14)
( 12)
{ 5)
< 9)
( 9)
( 20)
< 17)
( 14)
( 3)
« 8)
( 23)
INJE
NO
311
5<»0
406
196
Io2
163
391
46tt
42a
168
506
50b
229
210
162
343
223
Ib5
217
241
174
389
448
363
75
216
415
-------
L6«ES BANKED BY INDE* NOS.
LAKE CODE LAKE NAME
INDE* N
1 4901 BE** LAKE 540
i 4911 NAVAJO LAKE 506
3 4910 MOON LAKE 506
4 4907 HUNTINGTON NORTH RESERVO 468
5 4922 STEINAKER RESERVOIR 448
6 4908 JOE'S VALLEY RESERVOIR 428
7 5605 FLAMING GORGE RESERVOIR 415
8 4902 LOWER BOKN'S RESERVOIR 406
9 4906 FISH LAKE 391
10 4921 STARVATION RESERVOIR 389
11 4923 TROPIC RESERVOIR 363
12 4915 PELICAN LAKE 343
13 0408 LAKE POWELL 311
14 4919 PRUESS RESERVOIR 1GARRIS 241
15 4912 NEWCASTLE RESERVOIR 229
16 4916 PINEVIEW RESERVOIR 223
17 4918 PORCUPINE RESERVOIR 217
18 4925 HILLARO BAY RESERVOIR 216
19 4913 OTTER CREEK RESERVOIR 210
20 4903 DEER CREEK RESERVOIR 196
21 <»920 SEVIER BRIDGE RESERVOIR 174
22 4909 MINERSVILLE RESERVOIR 168
23 4917 PIUTE RESERVOIR 165
24 4905 LYNN RESERVOIR 163
25 4914 PANQUITCH LAKE 162
26 4904 ECHO RESERVOIR 152
-------
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"4 = 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 UTAH
LAKE CODE 4916 PINEVIEw RES
TOTAL DRAINAGE AREA OF LAKE(SO KM) 802.9
10/13/76
SUB-DRAINAGE
TRIBUTARY AREAtSd KM)
4916A1
491631
4916CI
491601
4916E1
4916F1
4916G1
4916H1
4916ZZ
JAN
FEB
APR
MAY
NORMALIZED FLO«S
JUS JUL AUG
SEP
OCT
NOV
DEC
SUMMARY
TOTAL DRAINAGE AREA OF LAKE » 803.9
SUM OF SUB-DRAINAGE AREAS - 803.2
TOTAL FLO* IN
TOTAL FLO* OUT
57.54
75.55
MEAN MONTHLY FLOWS AND DAILY FLOWS(CMS)
TRIBUTARY MONTH YEAR MEAN FLOW DAY
4916A1
491681
11
12
1
2
3
4
5
6
7
a
9
10
11
12
1
2
3
4
5
6
7
8
9
10
74
74
75
75
75
75
75
75
75
75
75
75
74
74
75
75
75
75
75
75
75
75
75
75
O.S10
2.039
4.248
3.964
2.124
19.539
27.467
15.574
10.760
12.743
8.495
4.814
1.359
1.359
1.331
1.189
2.067
4.814
17.840
9.345
1.218
0.170
0.065
1.189
9
19
23
12
22
18
12
9
19
11
8
23
23
22
18
12
FLOW DAY
0.510
2.747
FLOW DAY
FLOW
30.016
20.105
24.069
7.646
13.026
1.359
1.388
1.359
1.133
8.495
24.069
6.796
0.906
0.113
23
34.547
MEAN
802.9
440.3
0.0
85.5
17.1
160.6
19.4
0.0
80.3
3.40
0.76
0.0
0.057
0.028
0.170
0.20
0.028
0.37
3.68
1.50
0.0
0.227
0.028
0.736
0.28
0.028
0.57
6.51
1.76
0.0
0.311
0.057
0.793
0.31
0.028
0.59
9.63
7.36
0.0
2.832
0.14£
4.248
0.37
0.028
0.71
13.88
10.19
0.0
3.115
0.283
4.248
0.42
0.057
0.82
7.93
2.55
0.0
0.396
0.283
1.416
0.45
0.057
0.91
9.06
0.54
0.0
0.028
0.227
0.142
0.25
0.142
0.51
7.93
0.28
0.0
0.006
0.227
0.028
0.20
0.142
0.37
5.95
0.23
0.0
0.014
0.170
0.057
0.20
0.113
0.40
2.78
0.20
0.0
0.006
0.057
0.0
0.17
0.085
0.34
2.27
0.31
0.0
0.003
0.028
0.0
0.20
0.057
0.40
2.55
0.74
0.0
0.057
0.028
0.198
0.23
0.028
0.42
6.32
2.20
0.0
0.589
0.130
1.000
0.27
0.066
0.53
-------
TPI8UTARV FLO* INFORMATION FOR UTAH
10/18/76
LAKE CODE 4916
PINEVIEW SES
MEAN MONTHLY FLO»S AND OAILY FLOwS(CMS)
TRIBUTARY MONTH YEAR
4916D1.
4916E1
4916F1
491601
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
g
9
10
11
12
1
2
3
4
5
6
7
8
9
10
74
74
75
75
75
75
75
75
75
75
75
75
74
74
75
75
75
75
75
75
75
75
75
75
74
74
75
75
75
75
75
75
75
75
75
75
74
74
75
75
75
75
75
75
75
75
75
75
MEAN FLOW DAY
0.227
0.057
0.028
0.028
0.566
1.841
7.362
0.850
0.057
0.028
0.014
0.057
0.023
0.028
0.028
0.028
0.057
0.113
0.283
0.425
0.283
0.227
0.170
0.057
0.011
0.170
0.003
0.003
0.283
1.982
13.3C9
8.495
0.623
0.142
0.057
0.011
0.283
0.227
0.227
0.198
0.566
0.368
0.425
0.821
0.566
0.340
0.283
0.340
9
19
11
8
23
23
22
18
12
9
19
11
8
23
23
22
18
12
FLO* DAY
0.227
0.057
0.028
0.028
5.097
6.796
0.708
0.057
0.028
FLO* DAY
FLO«
0.011
0.170
0.003
0.003
5.663
12.743
5.663
0.396
0.170
-------
TRIBUTARY FLO* INFORMATION FOS UTAH
10/16/76
LAK:E CODE 4916 PINEVIE* »ES
MEAN MONTHLY FLOwS AND DAILY FLOWS(CMS)
TRIBUTARY
4916H1
4916ZZ
MQNTH YEAR
11
12
1
2
3
4
5
6
7
a
9
10
11
12
1
2
3
4
5
6
7
8
9
10
74
74
75
75
75
75
75
75
75
75
75
75
74
74
75
75
75
75
75
75
75
75
75
75
MEAN FLOW DAY
0.057
0.028
0.028
0.028
0.028
0.028
0.028
0.057
0.113
0.142
0.142
0.113
0.934
0.736
0.736
0.651
1.869
1.218
1.388
2.690
1.869
1.104
0.934
1.104
FLO« DAY
FLO* OAY
FLOU
-------
APPENDIX D
PHYSICAL and CHEMICAL DATA
-------
491601
4l 15 19.0 111 50 21.0 3
4*05? uTan
11E?ALES 760109 2111203
0055 FEET DEPTH CLASS 00
00010
*ATER
TEMP
CENT
9.5
9.2
8.-?
8.2
7.0
21.5
21.*
20.0
13.5
11.9
11.1
18.2
ltt.1
18.1
18.1
17.0
00300
DO
MG/L
9.0
n.o
10.6
10.*
9.6
5.2
4.2
2.0
3.4
2.6
3.6
7.9
5.4
5.4
2,0
0.4
00077
TKANSP
SECCHi
INCHES
42
102
48
00094
CNOUCTVY
FIELD
MICROMHO
164
162
164
165
160
221
217
192
163
156
153
211
213
211
213
197
00400
r^H
su
8.50
8.50
8. 40
8.40
8.20
8.50
8.15
7.90
7.65
7.80
8.05
8.20
7.90
7.90
7.60
7.50
00410
T ALK
CAC03
MG/L
105
103
105
103
108
111
110
105
96
95
102
131
131
130
130
124
00610
NH3-N
TOTAL
MG/L
0.030
0.030
0.030
0.030
0.040
0.100
0.230
0.100
0.050
0.120
0.130
0.020
0.020K
0.020K
0.120
0.160
00625
TOT KJEL
N
MG/L
0.700
0.500
0.400
0.500
0.300
0.500
0.600
0.500
0.400
0.500
0.500
0.200
0.200
0.200
0.500
0.500
00630
N02&N03
N- TOTAL
MG/L
0.290
0.330
0.370
0.360
0.460
0.160
0.160
0.300
0.400
0.460
0.390
0.030
o.oao
0.030
0.090
0.060
00671
PHOS-DIS
OHTnO
MG/L P
0.016
0.010
0.015
0.008
0.015
0.006
0.007
0.005
0.005
0.015
0.018
0.004
0.003
0.003
0.014
0.012
DATE
FROM
TO
75/05/14
75/08/07
75/09/23
00665 32217 00031
TIME DEPTH PHOS-TOT CHLRPHYL INCDT LT
OF A REMNING
DAY FEET
10
10
10
10
10
11
11
11
11
11
11
10
10
10
10
10
25
25
25
25
25
30
30
30
30
30
30
00
00
00
00
00
0000
0005
0010
0025
0051
0000
0005
0016
0030
0050
0068
0000
0005
0015
0035
0061
MG/L P
0
0
0
0
0
c
0
0
0
0
0
0
0
0
0
0
.050
.051
.042
.039
.023
.027
.028
.023
.024
.036
.040
.026
.020
.022
.076
.090
UG/L PERCENT
15.6
2.5
2.7
-------
STJ-ET -
15 26sO 111
,0 3
49057 UTAH
150731
OATE
FROM
TO
75/05/14
75/08/07
75/09/23
TIMf DEPT-t
Of
DAY FEET
10 50
10 50
10 50
10 50
11 00
11 00
11 00
11 00
11 00
09 45
09 45
09 45
09 45
0000
0005
0015
0019
0000
0005
0016
0030
0041
0000
0005
0015
0024
00010
WATER
TEMP
CENT
10.0
9.5
7.7
7o4
23.3
23.1
?2.7
15.4
13.6
18.3
18.6
18.5
18.5
11E3<
VLES
211
0023 FEET 0£PTH CLASS
00300
00
*»G/L
9.4
10oO
9«4
1006
7.2
7.2
6.8
2.4
3aO
7.8
6.6
6.2
6.2
00077
TRANSP
SECCHI
INCHES
22
96
60
0009^
CNOUCTVY
FIELD
MICROMHO
166
166
160
160
237
230
225
190
165
219
222
221
221
00400
PH
SU
8.70
8^45
8.20
8.50
8.70
8,70
8.60
8.00
7.90
8.10
8.10
8.10
8.10
00410
T ALK
CAC03
MG/L
106
105
104
105
113
112
110
104
101
131
133
134
131
00610
NH3-N
TOTAL
MG/L
0.040
0=040
0.040
0.640
0.270
0.140
0.100
0.080
0.060
0.020
0.020
0.030
0.020
1202
00
00625
TOT NJEL
N
MG/L
0.400
OeSOO
0.400
0.600
0.400
0.400
0.500
0.560
0*500
0.200
0.200
0.200
0.200
00630
N02&M03
N-TOTAL
MG/L
0.220
0.280
0.340
0.250
0.030
0.040
0.060
0.350
0.400
0.040
0.030
0.040
0.030
00671
PMOS-OIS
ORTHO
MG/L P
0.007
0.006
0.008
0.007
0.006
0.004
0.004
0.009
0.011
0.004
3.005
0.007
0.005
DATE
FROM
TO
75/05/14
75/08/07
75/09/23
00665 32217 00031
TIME DEPTH PHOS-TOT CHLRPHVL INCDT LT
OF A REMNING
DAY FEET
10
10
10
10
11
11
11
11
11
09
09
09
09
50
50
50
50
00
00
00
OQ
on
45
45
45
45
0000
0005
0015
0019
0000
0005
0016
0030
0041
0000
0005
0015
0024
MG/L P
0.
0.
0.
0,
0.
0,
0,
0,
0,
0.
0,
0,
0.
,070
,063
.059
.078
.029
.028
.023
,032
,032
.021
.028
,032
,028
JG/L PERCENT
7»0
4.1
3.2
-------
STC/xET "ET^IEvAL DATE ?t/:?
491003
•»! Ib 17.0 111 47 41.0 3
«*9057 UTAH
760109 2111202
0046 FEET DtPTH CLASS 00
DATE
FROM
TO
75/05/14
75/08/07
75/09/23
00010
TI*E DEPTH wATER
OF TEMP
DAY FEET
11 15
11 15
11 15
11 15
1 50
1 50
1 SO
1 50
1 50
09 30
09 30
09 30
09 30
0000
0005
0026
0042
0000
0005
0015
0030
0055
0000
0005
0015
0038
CENT
10.3
9.1
6.9
6.3
22.9
22.6
22. -3
16.0
12.4
16.5
18.6
IB. 6
IB. 3
00300 00077 00094
00 TtfANSP CNOUCTvr
SECCMI FIELD
MG/L INCHES MICeOMHO
11.0
10.8
9.0
9.0
6.4
6.2
6.6
0.6
1.6
6.9
6.6
6.2
5.6
31 161
150
150
160
90 221
225
225
179
161
96 218
218
218
223
00400 00*10
PH T ALK
CAC03
su
9.00
8.70
8.20
6.20
8.80
B.80
a. 75
8.00
8.00
8.10
8.10
8.00
B.05
MG/L
107
93
109
109
111
112
113
105
99
129
130
130
133
00610 00625 00630 00671
NH3-N TOT K.JEL N02kN03 PnOS-DIS
TOTAL N N-TOTAL OUTHO
MG/L
0.040
0.030
0.070
0.070
0.040
0.090
0.060
0.080
0.060
0.020K
0.020
0.030
0.040
MG/L
0.600
0.600
0.400
0.400
0.500
0.600
0.600
0.500
0.500
0.300
0.300
0.400
0.400
MG/L
0.160
0.280
0.480
0.490
0.100
0.070
0.070
0.350
0.440
0.040
0.040
0.040
0.040
MG/L P
0.005
0.008
0.013
0.012
0.005
0.004
0.006
0.005
0.017
0.002K
0.005
0.005
0.008
00665 32217
DATE TIME DEPTH PHOS-TOT CHLRPHVL
FROM OF A
TO DAY FEET MG/L P UG/L
75/05/14 11 15 0000 0.053 5.0
1 15 0005 0.052
1 15 0026 0.024
1 15 0042 0.024
75/08/07 1 50 0000 0.019 4.5
1 50 0005 0.019
1 50 0015 0.019
11 50 0030 0.020
11 50 0055 0.034
75/0-J/23 09 30 0000 0.029 4.3
09 30 0005 0.026
09 30 0015 0.027
09 30 0038 0.055
00031
INCOT LT
REMNING
PERCENT
K VALUE KNUWN TO BE.
LESS THAN INDICATED
-------
•+91604
41 16 33.0 111 48 52.0 3
49057 UTAH
11EPALES 760109 2111202
0029 FEET OtPTri CLASS 00
DATE
FROM
TO
75/05/14
75/08/07
75/09/23
TIME
OF
DAY
11 40
11 40
11 40
11 40
12 20
12 20
12 20
12 20
12 20
09 10
09 10
09 10
09 10
DEPTH
FEET
0000
0005
0015
0024
0000
0005
0015
0025
0040
0000
0005
0015
0027
00010
• ATER
TEMP
CENT
11.3
8.3
7.1
6.7
23.7
23.8
21.1
16.1
12.9
18.6
18.5
14.5
18.5
00300
00
MG/L
9.8
10.2
9.2
9.8
7.2
7.0
3.8
2.0
2.2
6.4
6.4
6.2
6.2
00077
TRAI
*SP
SECCnl
INCHES
24
72
96
00094
CNDUCTVY
FIELD
MICHOMHG
147
145
140
125
225
225
207
179
157
216
217
217
217
00400
Ph
su
8.90
8.20
8.00
8.70
8.90
8.90
8.30
8.00
8.00
8.10
8.10
8.10
8.10
00410
T ALK
CAC03
MG/L
35
93
87
91
111
110
113
102
99
129
128
127
131
00610
NH3-N
TOTAL
MG/L
0.040
0.030
0.030
0.030
0.060
0.360
0.410
0.340
0.200
0.020K
0.020K
0.030
0.020
00625
TOT KJEL
N
MG/L
1.100
0.400
0.4QO
0.600
0.600
0.600
0.700
0.500
0.500
0.300
0.300
0.300
0.400
00630
N02&N03
N-TOTAL
MG/L
0.390
0.530
0.610
0.390
0.110
0.090
0.180
0.340
0.400
0.040
0.040
0.040
0.040
00671
PHOS-DIS
ORTHO
MG/L P
0.015
0.007
0.014
0.009
0.005
0.006
0.003
0.004
0.010
0.002K
0.002
0.002
0.002K
DATE
FROM
TO
75/05/14
75/08/07
75/09/23
00665 32217 00031
TIME DEPTH PHOS-TOT CHLRPHYL INCDT LT
OF A REMNING
DAY FEET
11
11
11
11
12
12
12
12
12
09
09
09
09
40
40
40
40
20
20
20
20
20
10
10
10
10
0000
0005
0015
0024
0000
0005
0015
0025
0040
0000
0005
0015
0027
MG/L P
0,
0,
0.
0.
0,
0,
0,
0
0,
0,
0.
0,
0,
.117
.035
.035
.051
.017
.017
.017
.019
.043
.018
.022
.026
.024
UG/L PERCENT
8.5
3.6
7.3
K V/ALUE KNOWN TO BE
LESS THAN INDICATED
-------
APPENDIX E
TRIBUTARY DATA
-------
STO«ET
DATE 76/06/12
DATE TIME DEPTH N02&N03
FROM OF
TO DAY FEET
74/11/09 10 50
74/12/19 1? 05
75/04/23 15 20
75/05/23 15 00
75/06/22 14 45
75/07/18 17 30
75/08/12 16 50
4916A1
H! IS 20.0 111 50 20.0 4
OGOEN RIVER
49 HEBER COUNTY MAP
O/PINEVIE* SESERVOI* 150791
BELOW PINEVIEK DAM <».5 MI £ OF OGOEN
11EPALES 2111204
0000 FEET DEPTH CLASS 00
0630
I&N03
OTAL
IG/L
0.128
0.272
0.590
0.375
0.480
0.130
0.520
00625
TOT KJEL
N
MG/L
0.500
0.600
0.150
2.400
0.200
0.100
0.200
00610
NH3-N
TOTAL
MG/L
0.130
0.015
0.015
0.120
0.135
0.035
0.005K
00671
PHOS-D1S
ORTHO
MG/L P
0.010
0.005K
0.020
0.025
0.010
0.025
00665
PHOS-TOT
MG/L P
0.030
0.010
0.070
0.030
0.040
0.035
0.060
K VALUE KNOWN TO BE
LESS THAN INDICATED
-------
bTORET RETRIEVAL DAT?: 76/Od/13
DATE TIME DEPTH N02&N03
FROM OF
TO DAY FEET
74/11/09
74/13/19
75/01/11
75/03/08
75/04/33
75/05/23
75/06/22
75/07/18
75/08/12
75/09/14
11 15
10 40
13 00
13 00
15 30
08 10
14 55
17 00
09 30
491b81
41 14 50.0 111 45 45.0 4
S B« S FK OGDEN ^IVES
49 *Eb£R COUNT r MAP
T/PINEVIE* RESERVOIR
RT 39 6ROG 9 Ml E
llt^ALES
150791
uF OGOEN
211120*
0000 FEET DEPTH CLASS 00
0630
&N03
OTAL
G/L
0.208
0.368
0.480
0.448
0.640
1.050
0.530
C.330
0.340
1.500
00625
TOT KJEL
N
MG/L
0.100
0.100
0.600
0.600
0.550
1.500
0.750
0.150
0.100
0.200
00610
NH3-N
TOTAL
MG/L
0.025
0.005K
0.010
0.016
0.015
0.040
C.030
0.025
0.005K
0.015
00671
PHOS-OIS
ORTHO
MG/L P
0.030
0.015
0.020
0.016
0.035
0.030
0.040
0.020
0.020
0.010
00665
PHOS-TOT
MG/L P
0.050
0.020
0.040
0.020
0.190
0.050
0.020
0.030
0.020
K VALUE KNOWN TO BE
LESS THAN INDICATED
-------
OATE 7&/06/12
4916C1
41 15 00.0 111 45 35.0 4
N tj(J S F* OGOEN
DATE
FROM OF
TO DAY
TIME DEPTH
FEET
74/11/09
74/12/19
75/01/11
75/02/08
75/04/23
75/05/23
75/06/22
75/07/18
75/08/12
75/09/14
12 35
10 50
13 15
13 20
15 35
08 15
15 00
17 40
17 10
09 45
00630
N02&N03
N-TOTAL
MG/L
0.168
0.168
0.200
0.288
0.500
C.660
C.460
0.510
0.375
1.375
00625
TOT KJEL
N
MG/L
0.200
0.100K
0.100
0.900
0.200
1.450
0.700
0.150
0.100K
0.400
00610
NH3-N
TOTAL
MG/L
0.030
0.005
O.OOSK
0.024
0.010
0.030
0.030
0.010
O.OOSK
0.005
00671
PHOS-DIS
ORTHO
MG/L P
0.015
O.OOSK
0.010
0.008K
0.015
0.010
0.030
0.005
O.OOS
0.010
49 aE
T/PINEVIEW
«T 39 BROG
11EPALES
0000 FEET
00665
PHOS-TOT
MG/L P
0.015
0.010K
0.020
0.010
0.070
0.020
0.010K
0.010K
0.040
COUNTY MAP
150791
OF OGOEN
2111304
DEPTn CLASS 00
.1 MI E
K VALUE ivJOrtN TO BE
LESS THAN INDICATED
-------
RETRIEVAL DATE 76/04/12
491601
4i 17 15.0 111 46 37,0 4
*IDOi-£ FO-<* OGDEN rflvE*
49 7o5 HUNTSVILLE
T/PINEvIEn ^EStRvOI" 1507^1
7100 E *T 6ROG 2 MI U OF HUNTSVILLE
IIEP^LES 2111204
0000 FEET DEPTH CLASS 00
DATE
FROM OF
TO DAY
TIME DEPTH
FEET
74/11/09 12 20
74/12/19 11 25
75/01/11 13 50
75/02/08 13 45
75/04/23 15 50
75/05/23
75/06/22 15 40
75/07/18
75/08/12 17 20
00630
N02&N03
N-TOTAL
MG/L
0.136
0.072
0.112
0.624
0.575
0.240
0.300
0.135
0.210
00625
TOT KJEL
M
MG/L
0.300
0.200
0.700
0.500
0.400
0.600
0.500
0.150
0.100K
00610
NH3-N
TOTAL
MG/L
0.035
0.045
0.010
0.016
0.090
0.180
0.025
0.030
0.005K
00671
PHOS-OIS
ORTHO
MG/L P
0.010
0.005K
0.005K
0.008K
0.010
0.010
0.015
0.005
0.010
00665
PHOS-TOT
MG/L P
0.010
0.010K
0.010K
0.010K
0.070
0.010
0.010K
0.030
K VALUE KNO^N TO d£
LESS THAN INDICATED
-------
STjftET
DAT- 7s/0a/12
4916E1
41 17 35.0 111 47 15cO 4
3EKTSEN CREEK
*9 *E3EH COUNTY MAP
T/PINEVIE* -?ESERvOIR 150791
«T 166 B«OG 2 MI ENE OF EDEN
IIE-^ALES 211120H
0000 FEET DEPTH CLASS 00
DATE TIME OEPTn
FROM OF
TO DAT FEET
74/11/09 12 30
75/02/08 14 00
75/04/23 16 00
75/05/23
75/06/22 15 50
75/07/1U
75/09/14 10 15
00630
N02iN03
N-TOTAL
MG/L
0.200
0.352
0.270
0.730
0.780
9.220
1.075
00625
TOT KJEL
N
MG/L
0.300
0.600
0.350
0.500
0.350
O.?50
0.300
00610
NH3-N
TOTAL
MG/L
0.115
0.040
0.035
0.040
0.025
0.005
0.030
00671
PHOS-OIS
ORTrlO
MG/L P
0.035
0.032
0.015
0.030
0.010
0.065
0.050
00665
PHOS-TOT
MG/L P
0.040
0.040
0.090
0.060
0.070
0.130
0.100
-------
5T3RET
4916F1
41 17 14.0 111 49 10.0 4
NORTrs FOKK OGOEN RI*E3
49 7.5 rtU\TSVILL£
T/PINEVIE* RESE«vOI-< 150791
ST RT 162 8KOG 1.5 MI S OF EOEN
11EPALES 211120*
0000 FEET DEPTH CLASS 00
DATE
FROM
TO
74/11/09
74/12/19
75/0 I/ 11
75/02/08
75/04/23
75/05/23
75/06/22
75/07/18
75/09/14
00630 00625
TIME DEPTH N02&N03 TOT KJEL
OF N-TOTAL N
DAY FEET
13
11
14
14
16
16
10
00
50
05
30
10
00
30
MG/L
0
0
0
0
0
1
0
0
0
.520
.672
.760
.768
.990
.570
.750
.770
.985
MG/L
0.600
0.10GK
0.100K
0.300
0.650
0.400
0.350
0.100
0.800
00610 00671 00665
NM3-K PriOS-DIS PHOS-TOT
TOTAL ORTHO
MG/L
0.
0.
0.
0.
0.
0.
0.
0.
0.
030
005K
005
016
010
010
035
005K
050
MG/L
0.
0.
0.
0.
0.
0.
0.
0.
0.
P
010
005K
005K
008K
025
010
070
010
OCSK
MG/L P
0
0
0
0
0
0
0
0
.010
.010K
.010
.010K
.030
.080
.030
.010K
K V4LUE M>iOWN TO BE
Lt.5S THAN INDICATED
-------
STO^ET RE
3AT£ 7b/OS/12
DATE
FROM OF
TO DAY
TIME DEPTM
FEET
13 10
11 00
75/01/11 13 00
75/03/08 13 30
75/OV33 15 40
75/05/33
75/06/32 15 30
41 It 00.0 111 4fc J5.0 4
SPSING C«£E*
«f9 7.5 nUNTSVILLE
T/PINEVIE* SESERVOI* 150791
BRDG OM 7100 EAST ST IN NO»TH HUNTSVlLLE
IIE^ALES 2111204
ooco FEET DEPTH CLASS oo
00630
N02«.N03
N-TOTAL
MG/L
0.464
0.552
0.400
O.S04
1.500
1.000
2.300
00625
TOT KJEL
N
MG/L
0.700
0.200
0.200
1.000
0.450
0.650
0.350
00610
NH3-N
TOTAL
MG/L
0.040
0.010
0.030
0.046
0.095
0.015
0.015
00671
PHOS-DIS
ORTHO
MG/L P
0.025
0.005K
0.010
0.016
0.050
0.020
0.005
00665
PhOS-TOT
MG/L P
0.060
0.040
0.060
0.070
0.090
0.040
0.030
K VALUE KNOnl-J TO 6£
LESS THAN INDICATED
-------
17 15.0 111 46 37.0 4
CANAL
;»•} 7.5 MUNTSVILLc.
T/Pp.EVlE* 3ESESVOH 150791
630G ON 7100 EAST ST .2 MI N OF HUNTSVlL
11EPAL6S 211120*
0000 FEET OEPTh CLASS 00
'ATE TIME OE0T-i
rt»OM OF
TO DAY FEET
7'./ 11/09 12 00
7<«'12/19 11 05
7'-/01/H 13 35
7'.'02/08 13 35
7'./04/23 15 45
7'./05/23 08 30
7'./06/22 15 05
00630
N026N03
N-TOTAL
MG/L
0.240
0.540
0.432
0.504
0.185
0.352
0.230
00625
TOT KJEL
N
MG/L
0.800
0.250
0.500
0.600
0.400
2.000
0.300
00610
NH3-N
TOTAL
MG/L
0.040
0.210
0.020
C.032
0.005K
0.037
0.010
00671
PHOS-OIS
ORTHO
MG/L P
0.030
0.010
0.015
0.016
0.025
0.030
C.015
00665
PrtOS-TOT
MG/L P
0.030
0.020
0.030
0.030
0.040
0.040
K VALUE KNOW, TO o£
LESS TMAN INDICATED
------- |