-------
DEER CREEK RESERVOIR
Tributary Sampling Site
X Lake Sampling Site
Sewage Treatment Facility
15
-------
DEER CREEK RESERVOIR
STORE! NO. 4903
I. CONCLUSIONS
A. Trophic Condition:
Survey data indicate that Deer Creek Reservoir is eutrophic.
It ranked twentieth in overall trophic quality among the 27 Utah
lakes and reservoirs sampled in 1975 when compared using a com-
bination of six water quality parameters*. Fifteen of the water
bodies had less median total phosphorus, ten had less and three had
the same median dissolved orthophosphorus, 21 had less median inor-
ganic nitrogen, 17 had less mean chlorophyll a, and 15 had greater
mean Secchi disc transparency. Marked depression of dissolved oxy-
gen with depth occurred at sampling station 1 in August and September.
Survey limnologists noted submerged macrophytes near the shore-
line in August and clumps of algae at the surface in September, par-
ticularly at sampling station 3.
B. Rate-Limiting Nutrient:
The algal assay results indicate phosphorus limitation at the
times the samples were collected (05/12/75 and 09/19/75). The
reservoir data also indicate phosphorus limitation in May and Sep-
tember but nitrogen limitation at two of the three sampling stations
in August.
* See Appendix A.
-------
2
C. Nutrient Controllability:
1. Point sources—During the sampling year, point sources
contributed 48.5% of the total phosphorus input to Deer Creek
Reservoir. The wastewater treatment facilities at Midway and
Heber City accounted for 6.2% and 24.7%, respectively. The
Clearview Trout Farm added 2.9%, and the Midway Fish Hatchery
contributed 14'.7%; however, the proportion of these loads
attributable to the hatchery operations is not known since
the quality of the waters entering the hatcheries was not
measured.
The present phosphorus loading of 2.47 g/m2/year is 2.2 times
that proposed by Vollenweider (Vollenweider and Dillon, 1974) as
a eutrophic loading (see page 13). Because the reservoir is phos-
phorus limited much of the time, all phosphorus inputs should be
minimized to the greatest practicable degree. It is calculated
that the present phosphorus loading would have to be reduced 55%
to achieve a level equal to the proposed eutrophic loading.
2. Non-point sources—Non-point sources accounted for 51.5% of
the total phosphorus load during the sampling year. The Provo River
contributed 37.8%, and three other gaged tributaries collectively
contributed 11.3%. The ungaged minor tributaries and immediate
drainage accounted for an estimated 1.7% of the total load.
-------
II. RESERVOIR AND DRAINAGE BASIN CHARACTERISTICS1"
A. Morphometry :
1. Surface area: 9.66 kilometers2.
2. Mean depth: 19.9 meters.
3. Maximum depth: 41.8 meters.
4. Volume: 192.301 x 106 m3.
5. Mean hydraulic retention time: 211 days (based on outflow).
B. Tributary and Outlet:
(See Appendix C for flow data)
1. Tributaries -
Drainage Mean flow
Name area (km2)* (m3/sec)_*
Provo River (includes area & flow
of Spring Creek) 976.4 8.230
Decker Creek 4.7 0.011
Snake Creek 82.9 1.300
Daniels Creek 126.9 0.100
Main Creek 186.5 0.375
(Spring Creek) (150.2) (0.510)
Minor tributaries &
immediate drainage - 63.3 0.660
Totals 1,440.7 10.676
2. Outlet -
Provo River 1,450.4** 10.540
C. Precipitation***:
1. Year of sampling: 123.1 centimeters.
2. Mean annual: 110.0 centimeters.
t Table of metric conversions—Appendix B.
tt Sudweeks, 1975; max. depth from Ikner (1974).
* For limits of accuracy, see Working Paper No. 175, "...Survey Methods,
1973-1976".
** Includes area of reservoir.
*** See Working Paper No. 175.
-------
4
III. WATER QUALITY SUMMARY
Deer Creek 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 three stations on the reservoir (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 _a
analysis. The maximum depths sampled were 35.1 -meters at station
1, 24.4 meters at station 2, and 5.5 meters at station 3.
The sampling results are presented in full in Appendix D and
are summarized in the following table.
-------
(0 5.0
DISS OXY (MG/L) 8.6
CNDCTYY (MC> 294.
PH (STAND UNITS) 8.3
TOT ALK (MG/D 136.
TOT P (MG/L) 0.027
ORTHO P (MG/L) 0.006
N02*N03 (MG/L) 0.180
AMMONIA (MG/L) 0.030
KJEL N (MG/L) 0.300
INORG N (MG/L) 0.210
TOTAL N (MG/L) 0.50C
CHLRPYL A (Ufi/L) 4.3
SECCHI (METERS) 1.1
A0 iU-l'-'ArSY Of PHYSICAL AND
1ST SAMPLING ( 5/12/75)
1 SITES
4NGL MEAM MEDIAN
905 70*> 3.2
" 11.0 9.7 9.7
316. 306, 307.
8.7 8.5 8.5
- 149. 144. 145.
- 0.054 0.040 0.042
- 0.021 0.012 0.012
- 0.270 0.213 0.200
- 0.180 0.071 0.040
- 0.600 0.464 0.450
- 0.450 0.284 0.230
- 0.870 0.677 0.675
9.3 7.4 8.5
l.d 1.5 1.8
FC.i
ER CPEEK S£SE«VOIR
STC.-JET COOE
2MO SAMPL
3 '-
KANbE
12.7 - 23.8
2.6 - 9.0
21b. - 333.
7.8 - 9.4
106. - 126.
0.020 - 0.089
0.002 - 0.058
0.020 - 0.390
0.020 - 0.040
0.200 - 0.500
0.040 - 0.410
0.220 - 0.670
1.3 - 1.5
1.5 - 2.1
»NC3 \ 8/M/75)
ires
MEAN MEDIAE
19^,6 22.4
6.7
297.
8.4
115.
0.040
0.006
0.060
0.020
6.1
283.
8.5
115.
0.040
0.017
0.170
0.022
0.329 0.350
0.192 0.110
0.499
1.4
3RO SAMPLING ( 9/19/75)
3 SITES
1.9
0.505
1.3
2.1
RAKGt
:3s3 - 18.8
0.2 - 10.4
223. - 338.
7.5 - 8.8
120S - 158.
0.014 - 0.285
0.002 - 0.069
0.030 - 0.440
0.020 - 0.270
0.200 - 0.800
0.050 - 0.510
0.380 - 1.040
11.6 - 25.2
0.9 - 2.7
ME Aft
17.6
6.7
298.
8.2
143.
0.055
0.010
0.159
0.044
0.406
0.203
0.566
18.5
l.ri
KEjIAN
18.2
S.O
303.
8.3
145.
0.035
0.004
0.140
0.020
0.400
0.160
0.530
18.7
1.8
-------
B.
Biological Characteristics:
1. Phytoplankton -
Sampling
Date
05/12/75
08/11/75
09/19/75
Domi nant
Genera
1.
2.
3.
4.
5.
1.
2.
1.
2.
3.
4.
5.
Stephanodiscus sp.
Chroomonas sp.
Flagellates
Cryptomonas sp.
Asterionella sp.
Total
Fragilaria sp.
Sphaerocystis sp_.
Total
Aphanizomenon sp.
Chroomonas sp.
Flagellates
Stephanodiscus sp.
Coelosphaerium sp.
Other genera
Algal Units
per ml
5,047
3,426
2,100
700
74
11,347
7,571
55
7,626
2,365
377
240
69
69
102
2» Chlorophyll a_ -
Total
3,222
Sampling
Dato
05/12/75
08/11/75
09/19/75
Station
Number
1
2
3
1
2
3
1
2
3
Chlorophyll a
faig/1 )
8.5
9.3
4.3
1.5
1.3
1.3
11.6
18.7
25.2
-------
C. Limiting Nutrient Study:
1. Autoclaved, filtered, and nutrient spiked -
a. May sample -
Spike (rng/1)
Control
0.050 P
0.050 P + 1.0 N
1.0 N
b. September sample -
Ortho P
Cone, (mg/1)
Inorganic N Maximum yield
Cone, (mg/1) (mg/1-dry wt.)
0.015
0.065
0.065
0.015
0.299
0.299
1.299
1.299
3.3
11.7
20.5
2.0
Spike (mg/1)
Control
0.050 P
0.050 P + 1.0 N
1.0 N
Ortho P
Cone, (mg/1)
0.010
0.060
0.060
0.010
Inorganic N Maximum yield
Cone, (mg/1) (mg/1-dry wt.)
0.185
0.185
1.185
1.185
1.0
7.1
22.3
1.0
2. Discussion -
The control yields of the assay alga, Selenastrum capri-
cornutum, indicate the potential primary productivity of Deer
Creek Reservoir was moderately high at the times the samples
were collected. Also, in both assays the significant increase
in yields with the addition of phosphorus alone indicates the
reservoir was limited by phosphorus at those times. Note that
the addition of nitrogen alone in both assays resulted in yields
no greater than those of the controls.
The reservoir data indicate phosphorus limitation in May
and September as well; i.e., the mean inorganic nitrogen/ortho-
-------
8
phosphorus ratios were 16/1 or greater at all stations in May
and 13/1 or greater at all stations in September. However,
nitrogen limitation is indicated at two of the three stations
in August; i.e., the mean N/P ratios were 9/1 at station 1 and
5/1 at station 3. The mean N/P ratio was 21/1 at station 2 in
August, and phosphorus limitation would be expected.
-------
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), except for the high
runoff months of ^ay and June when two samples were collected.
Sampling was begun in November, 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
Lha Utah District Office of the U.S. Geological Survey for the
tributary sites nearest the reservoir.
Except for Snake and Decker creeks, 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.
The combined nutrient loads of the Midway wastewater treatment plant
and the Midway Fish Hatchery exceeded the loads measured in Snake Creek at
station O'l; a^id, although Decker Creek was sampled nine times at station
B-ls most of the flows were too low to be measured accurately. Therefore,
the loads for these streams and the unsampled "minor tributaries and
immediate drainage" ("II" of U.S.G.S.) were estimated using the means of
tSis nutrient loads, in kg/km2/year, at stations D-l and E-l and multiplying
the means by the B~l, C-l, and ZZ areas in km2.
* See Working Paper No. 175.
-------
10
Also, the nutrient loads measured in Spring Creek at station F-l
are included in the Provo River loads at station A-2 and, hence, are
not listed separately in the loading tables that follow.
The operators of the Heber City and Midway wastewater treatment
plants provided monthly effluent samples and corresponding flow data,
a;;c! the personnel of Clearview Trout Farm and the Midway Fish Hatchery
provided monthly discharge samples and corresponding flows.
A. Waste Sources*:
L Known municipal -
Name
Hsber City
Midway
Pop.
Served
3,000
1,000
Treatment
tr. filter
tr. filter
Mean Flow
(mVd)
9,490.0
1,106.9
Recei vi ng
Water
Spring Creek/
Provo River
Snake Creek
2o Known Industrial - None
3. Fish hatcheries -
N
C
M
are
Isarview
Farm
Idway F1
Hatchery
Trout
sh
Type
Waste
fish prop-
agation
fish prop-
agation
Treatment
none
none
Mean Flow
(mVd)
11
76
s
>
255.
200.
3
2
Receiving
Water
Provo
Snake
River
Creek
••* Hopkins and Hinshaw, 1974.
-------
11
B. Annual Total Phosphorus Loading - Average Year:
1. Inputs -
kg P/ % of
Source y_r total
a. Tributaries (non-point load) -
S;rovo River 9,005 37.8
Decker Creek 30 0.1
Snake Creek 540 2.3
Daniels Creek 760 3.2
Main Creek 1,380 5.8
b. Minor tributaries & immediate
drainage (non-point load) - 410 1.7
GO Known municipal STP's -
Heber City 5,875 24.6
Midway 1,485 6.2
d» Septic tanks - Unknown ?
e0 Known industrial - None
f. Fish hatcheries -
Clearview Trout Farm 695 2.9
Midway Fish Hatchery 3,500 14.7
o. Direct precipitation* - 170 0.7
Total 23,850 100.0
2, Outputs -
Lake cutlet - Provo River 15,605
3o Net annual P accumulation - 8,245 kg.
* Sea Werkiiig Fapar No. 175.
-------
12
C. Annual Total Nitrogen Loading - Average Year:
1. Inputs -
kg N/ % of
Source y_r total
a. Tributaries (non-point load) -
Provo River 199,385 64.0
Decker Creek 240 0.1
Snake Creek 4,270 1.4
Daniels Creek 4,405 1.4
Main Creek 12,655 4.1
b. Minor tributaries & immediate
drainage (non-point load) - 3,260 1.0
c. Known municipal STP's -
Heber City 25,030 8.0
Midway 4,680 1.5
d. Septic tanks - Unknown ?
e. Known industrial - None
f. Fish hatcheries -
Clearview Trout Farm 6,190 2.0
Midway Fish Hatchery 40,810 13.1
g. Direct precipitation* - 10.430 3.3
Total 311,355 100.0
2. Outputs -
Lake outlet - Provo River 242,720
3. Net annual N accumulation - 68,635 kg.
D. Non-point Nutrient Export by Subdrainage Area:
Tributary kg P/km2/yr kg N/km2/yr
Provo River 9 204
Daniels Creek 6 35
Main Creek 7 68
* See Working Paper No. 175.
-------
13
E. Mean Nutrient Concentrations in Estimated or Unlisted Streams:
Mean Total P Mean Total N
Tributary Cone, (mg/1) Cone, (mg/1)
Decker Creek 0.059 0.324
Snake Creek 0.090 1.282
Spring Creek 0.300 1.492
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 2.47 0.85 32.2 7.1
Vollenweider phosphorus loadings
(g/m2/yr) based on mean depth and mean
hydraulic retention time of Deer Creek Reservoir:
"Dangerous" (eutrophic loading) 1.12
"Permissible" (oligotrophic loading) 0.56
-------
14
LITERATURE REVIEWED
Anderson, Donald R., John A. Dracup, Thomas J. Fogarty, and Robert
Willis; 1976. Water quality modeling of deep reservoirs.
Jour. Water Poll. Contr. Fed. 48 (1): 134-146.
Hopkins, Clyde M., and R. Hinshaw, 1974. Personal communications
(treatment plant questionnaires). UT Bur. of Env. Health, Salt
Lake City.
Ikner, James, 1975. Personal communication (max. depth of Deer
Creek Res.). U.S. Geol. Surv., Salt Lake City.
Sudweeks, Calvin K., 1974. 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
inland Waters, Burlington, Ontario.
-------
15
APPENDIX A
LAKE RANKINGS
-------
LAKE DATA YO E£ USEO IN RANKINGS
LAKE
CuDE LAKE
&403 LAKE POWELL
4931 BEAR LAKE
49y2 LOa'ER BOWN'S RESERVOIR
49J3 DEER CREEK RESERVOIR
4904 ECHO RESERVOIR
4905 LYNN RESERVOIR
4906 FISH LAKE
4907 HUNTINGTON NORTH RESERVO
4903 JOE'S VALLEY RESERVOIR
4',C9 *IMERSVILLE RESERVOIR
49 iw M;,GN LAKE
49 ii NAVAJO LAKE
4912 NEWCASTLE RESERVOIR
4913 OTTER CREEK RESERVOIR
4914 PANSUITCH LAKE
*.*i5 PELICAN LAKE
491& PINEVIEW RESERVOIR
4917 PIUTE RESERVOIR
49i3 PORCUPINE RESERVOIR
4919 PRLJESS RESERVOIR (GARRIS
4920 SEVIER BRIDGE RESERVOIR
4921 STARVATION RESERVOIR
4922 STEINAKSR RESERVOIR
4923 TROPIC RESERVOIR
4924 UTAH LAKE
4925 WILLAKO 8AY RESERVOIR
5605 FLAMING GORGE RESERVOIR
MEDIAN
TOTAL P
0.0^0
C.Ola
0.031
O.C38
0.047
0.121
C.023
C.OI3
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
0.132
0.044
0.011
MEDIAN
INORS N
0.410
0.040
0.0'*0
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
589-
MF.AN SEC
339.830
253.167
336.050
430.333
450.333
417.667
152.000
392.000
400.000
445.000
381.000
363.000
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
CHLORA
3.0S1
0.945
5.567
9.D78
6.967
39.600
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-
H!N DO
13.800
9.200
9.400
14.800
14.000
10.400
10.400
7.800
11.200
8.600
9.600
6.000
13.600
10.600
14.200
8.400
14.600
11.600
12.400
8.800
12.400
13.200
12.600
8.400
11.400
11.000
10.400
MEDIAN
01 SS ORTHO P
0.007
0.003
0.006
0.006
0.012
0.052
0.004
0.005
0.003
0.107
0.002
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 toZ7fi HIGhFR VALUES (NUMBER OF LAK5.S WJTH HIGHER VALUES)
CO^c. LAKE
040 d LA.<£ P
4901 BEAR LAKE
-*9i2 LOrfER «OsN'S RESERVOIR
4>;,,3 OSES CREEK RESERVOIR
4904 ECHO RESERVOIR
49CS LYfvlN RESERVOIR
4906 FISH LAKE
4907 HU.NTINGTO!.- NORTH RESERVO
4905 JOE'S VALLEY RESERVOIR
49u3 MINERSVILLE RESERVOIR
491C MOON LAKE
4911 MAVAJO LAKE
4912 NEWCASTLE RESERVOIR
4913 OTTER CREEK RESERVOIR
<*9l4 PA^HUITCH LAKE
4915 PELICAN LA;5
4 <
87 i
87 «
19 «
27 (
23 <
65 <
65 (
53 (
44 (
87 (
87 (
87 (
87 (
65 <
54 <
15 (
31 (
38 <
35 (
8 <
87 (
87 <
50 (
12 <
44 (
0 (
I)
19>
19)
S>
7)
6)
16i
16)
15)
11)
19)
19)
19)
19)
16)
14)
4)
8)
10)
9)
2)
19)
19)
13)
3)
11)
0)
500°
MEAN
•31
96
85
42
19
58
100
69
62
27
73
77
46
IS
50
35
38
8
31
0
23
65
88
54
4
12
92
SEC
( 21)
< 25)
{ 22)
( 11)
( 5)
( 15)
( 26)
( 18)
( 16)
( 7) '
( 19)
{ 20)
( 12)
( 4)
( 13)
( 9)
( 10)
( 2)
( 8)
< 0).
( 6>
( 17)
< 23)
( 14)
( 1)
( 3)
( 24)
MEAN
CHLGfiA
73 (
100 i
65 !
35 I
50 I
8 (
23 I
92 (
85 <
12 i
77 i
88 <
27 i
31 i
4 <
54 i
58 i
15 '
38 i
69 i
19 <
62 i
96 i
46
0 '
42 i
81 i
1 19)
I 26)
! 17)
t 9)
! 13)
1 2)
[ 6)
I 24)
1 22)
! 3)
1 20)
t 23)
i 7)
I 8)
I 1)
t 14)
t 15)
( 4)
( 10)
[ 18)
I 5)
( 16)
( 25)
( 12)
t 0)
t ID
I 21)
X5-
nZi
DISS GRTKO P Nv)
42 1
90 i
SO <
58 I
13 1
4 (
79 (
69 i
96 (
0 I
100 i
85 i
27 (
8 <
23 i
73 i
58 i
46 i
19 i
37 i
37 i
79 i
65 '
58
13 i
31
90 '
: .ID
! 23)
I 13)
I 14)
1 3)
E 1)
! 20)
t 18)
I 25)
I 0)
I 26)
I 22)
1 7)
( 2)
( 6)
( 19)
I 14)
( 12)
[ 5)
( 9)
t 9)
t 20)
t 17)
( 14)
( 3)
( 8)
( 23)
311
540
406
196
152
163
391
468
428
166
506
506
229
210
162
343
223
165
217
241
174
389
448
363
75
216
415
-------
LAKES k1 A:\.-.EJ- ~Y iN'OEx WOS.
8A?..< LAKE CODE LAKE N«M£ INDEX NO
i 4*0! c£AS LAKE 540
2 491; NAVAJO LAKE 506
3 -,910 HOONi LAX£ 506
t 4v07 nUNTlNSTON NiOftT.-l RESERVO 468
5 ^922 STEINAKER RESERVOIR 448
6 <'90a JOE'S VALLEY RESERVOIR 428
7 5i.05 FLAWING GORGE RESERVOIR 415
& ^9C2 LCn.'cS bOWN'S RESERVOIR 406
9 ^-JOc, flSH LAKE 391
1C ^v2i STARVATION RESERVOIR 389
II -v2C TROPIC F(£SERVGIR 363
12 49IS PELICAN LAKE 343
13 0408 LAKE POWELL 3il
14 4919 PRUESS RESERVOIR (GARRIS 241
IS 4912 NEWCASTLE RESERVOIR 229
ifc -.-^16 rT'jEVIEW RESERVOIR 223
17 4013 PORCUPINE RESERVOIR 217
IS 4C2S KlLLARD SAY RESERVOIR 216
i<) ^<-;i3 CTTE3 CREEK RESERVOIR 210
20 4v03 DEER CREEK RESERVOIR 196
21 <*920 SEVIER BRIDGE RESERVOIR 174
::?. ^>-:9 HITJEKSVILLE RESERVOIR 168
2o 49i? PIUTE RESERVOIR 165
24 4vOS LYNN' RESERVOIR 163
25 4914 ?A\aUITCH LAKE 162
25 49D- ECHO RESERVOIR 152
27 4924 UTAH LAKE 75
-------
APPENDIX B
CONVERSION FACTORS
-------
CONVERSION FACTORS
Hectares x 2.471 = acres
Kilometers x 0.6214 = miles
Meters x 3.281 = feet
-4
Cubic meters x 8.107 x 10 = acre/feet
Square kilometers x 0.3861 = square miles
Cubic meters/sec x 35.315 = cubic feet/sec
Centimeters x 0.3937 = inches
•
Kilograms x 2.205 s pounds
T
Kilograms/square kilometer x 5.711 = Ibs/square mile
-------
APPENDIX C
TRIBUTARY FLOW DATA
-------
TRIBUTARY F(_0w INFORMATION FOR UTAH
10/18/76
LAKt CODE
DEER CRK RES
TOTAL .JHAINAGE AREA OF LAKE (SO KM)
SUH-ORAINAGE
TRIBUTARY AREA
JUN JUL AUG
SEP
OCT
NOV
OEC
SUMMARY
TOTAL DRAINAGE AREA OF LAKE =
SUM OF SUB-DRAINAGE ARLAS =
1600.1
TOTAL FLOW IN
TOTAL FLOW OUT
134. 04
MEAN MONTHLY FLOWS AND DAILY FLOWS(CMS)
TRIBUTARY MONTH YEAR MEAN FLOW DAY
4903A1
FLO* DAY
FLOW DAY
FLOW
4903A2
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
4.757
9.203
8.164
5.947
3.710
10.024
12.856
40.068
22.342
15.574
13.819
6.768
5.097
3.681
3.964
3.964
4.531
5.380
21.521
40.210
14.725
5.947
3.964
5.947
10
14
11
8
8
5
3
7
12
16
13
5
10
14
11
8
8
5
3
7
12
9
13
4
3.030
10.845
8.269
8.240
2.520
10.137
9.713 17
46.723 21
28.883
16.509
14.696
11.327
4.814
4.i?14
4.248
4.?48
4.814
4.814
7.929 17
62.297 21
25.485
9.061
6.230
4.814
15.886
44.457
40.493
33.980
MEAN
4903A1
4903Ai
490331
4903C1
490 3D!
490 3E I
4903F1
490J.9
186.5
150.2
7?. 5
6.80
3.40
0.003
1.19
0.113
0.263
0.14
0.42
6.80
3.4Q
0.003
1.16
0.142
0.396
0.14
0.42
7.36
4.35
0.003
1.27
0.142
0.481
0.17
0.51
8.78
10.48
0.011
1.30
0.340
1.048
0.54
0.82
16.42
28.32
0.037
I.b9
0.227
1.104
1.61
1.70
24.35
25.20
0.037
1.67
0.028
0.311
1.73
1.70
15.01
6.80
0.017
1.27
0.003
0.102
0.74
0.54
12.18
3.40
0.008
1.10
0.006
0.088
0.31
0.31
10.19
2.83
0.006
1.10
0.011
0.091
0.23
0.28
5.95
3.11
0.006
1.30
0.028
0.139
0.20
0.34
5.38
3.68
0.003
l.Jfo
0.085
0.232
0.17
0.45
7.08
3.68
0.003
1.25
0.085
0.246
0.14
0.45
10.54
8.23
0.011
1.30
0.100
0.375
0.51
0.66
-------
TRIBUTARY FLQK INF0>"'UAT ION FOR UTAH
10/IS/76
LAKE C00£
GEE* CRC. ">ES
ME'-N MONTHLY FLO«S AND JAIL* FLOWS(CMS)
TRIB^TA^Y MONTH YEAf< MEAN FLOW DAY
490 Jdi
4903C1
490301
4903cl
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
2
3
4
5
6
7
8
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
74
74
75
75
75
75
75
75
75
75
75
75
0.003
0.003
0.003
0.003
0.003
0.003
0.028
0.076
0.051
0.017
0.008
0.006
1.982
1.133
1.133
1.416
1.699
2.265
1.699
2.549
1.133
0.850
0.850
1.416
0.113
0.085
0.113
0.113
0.198
0.368
0.368
0.003
0.011
0.017
0.113
0.198
0.142
0.227
0.227
0.283
0.283
0.538
1.614
0.481
0.340
0.227
0.170
10
14
11
8
d
5
3
7
12
9
13
5
10
14
8
5
3
7
12
9
13
5
10
14
11
8
8
5
3
7
12
9
13
5
FLO* DAY
FLOW DAY
FLOW
.671
.444
.396
.472
.812
2.010
2.152
2.832
2.237
1.048
1.161
1.104
0.963
0.085
0.113
0.198
0.198
0.991
0.003
0.014
0.023
0.028
0.198
0.170
0.227
0.227
0.283
0.227
0.311
1.699
0.566
0.368
0.255
0.170
17
21
17
21
17
21
2.067
2.832
0.368
0.283
0.510
1.133
-------
rcH UTA*
DAY
ti r* a. IT®
12 ?*• 0.142
1 T5 C.IA2
Z T5 fl.l*2
3 75 «.l*2
** 75 0.173
S 75 1.274
« 75 3.398
1 75 2.265
8 75 6.T36
» 75 S.425
I* 75 0.255
It 74 3.566
12 74 0.368
1 75 0.425
2 75 0.453
3 75 0.566
* 75 e.623
5 T5 1.642
6 75 2.718
1 75 1.019
8 75 0.425
9 75 0.340
U 75 0.510
-------
APPENDIX D
PHYSICAL and CHEMICAL DATA
-------
STC-^T PETRIFVAL DATE 7o/03/l2
D-TE
TO
75/05/12
75/03/1 I
75/09/19
COO 10
TIVF DEPTH »ATER
OF TEMP
UAY FEET
16 40 0000
16 40 0005
16 40 0025
16 40 0050
16 40 0075
16 40 0106
15 05 0000
15 05 0005
15 05 0020
15 05 0050
15 05 0085
15 05 Ollb
14 15 0000
14 15 0005
14 15 0015
14 15 0030
14 15 0050
14 15 0080
14 15 0115
CENT
a. 5
8.4
7.6
6.6
5.4
5.0
?3. 1
23.2
22. S
15.4
13.1
12.7
18.4
18. <*
17.9
17.8
17.8
15.3
13.3
00300
DO
MG/L
10.4
10.4
9.8
9.2
8.8
fl.6
7.2
7.0
6.4
3.8
3.2
2.6
8.0
8.0
7.2
7.0
6.2
1.0
0.2
00077
SECCHI FIELO
INCHES M]
72
84
108
490JO 1
40 24 J5.0 111 31 20.0 3
DEEP CREEK RESERVOIR
150791
11EPALES 2111202
0110 FEET DEPTH CLASS 00
94
TVY
1
•MHO
315
315
305
301
297
294
300
294
290
218
228
238
301
300
300
300
300
248
223
00400
PH
SO
8.65
8.70
8.60
8.40
8.35
8.30
8.70
8.60
8.20
7.90
7.80
7.80
8.45
8.40
8.30
8.10
8.00
7.60
7.50
00410
T ALK
CAC03
MG/L
145
145
147
149
148
148
115
116
115
113
112
114
143
145
142
141
141
126
120
00610
NH3-N
TOTAL
MG/L
0.040
0.040
0.080
0.120
0.130
0.180
0.020K
0.020
0.040
0.020K
0.020
0.020
0.020K
0.020K
0.020K
0.020K
0.020K
0.040
0.270
00625
TOT KJEL
N
MG/L
0.400
0.500
0.600
0.500
0.400
0.600
0.400
0.400
0.400
0.300
0.200K
0.200K
0.400
0.400
0.300
0.200
0.200
0.300
0.800
00630
N02fcN03
N-TOTAL
MG/L
0.190
0.190
0.210
0.250
0.270
0.270
0.070
0.070
0.090
0.370
0.380
0.390
0.130
0.130
0.150
0.180
0.200
0.440
0.240
00671
PHOS-OIS
OHTriO
MG/L P
0.006
0.006
0.011
0.013
0.014
0.021
0.008
0.005
0.007
0.044
0.050
0.058
0.004
0.003
0.002
0.002
0.004
0.024
0.069
* VALUE rv^OWN TO BE
LESS THAN INDICATED
-------
SETRIF.VAL DATE 76/os/i?
490301
40 24 35.0 111 31 20.0
DtEW CREEK RESERVOIR
49051 UTAH
150791
11EPAUES
0110 FEET
DEPTH
2111202
CLASS 00
00665 32217 00031
DATE TIME DEPTH PHOS-TOT CHLRPHYL liMCOT LT
FkuM OF A HEMMING
TO DAY FEET
7S/Ob/12 16
16
16
16
16
16
75/0 es/ 11 15
15
15
15
15
15
75/09/19 14
14
14
14
14
14
14
40
40
40
40
40
40
05
05
05
05
05
05
15
15
15
15
15
15
15
0000
0005
0025
0050
0075
0106
0000
0005
0020
0050
0085
0115
0000
0005
0015
0030
0050
0080
0115
MG/L P
0.
0,
0,
0,
0,
0.
0,
0,
0.
0.
0.
0.
0,
0,
0,
0.
fl<
0,
0,
.036
,044
.041
.032
.030
.054
,oae
.020
.020
.046
.066
.089
.019
.017
.016
.016
,OU
.087
.285
OG/L PERCENT
8.5
1.5
11.6
-------
490302
40 2t> 04.0 111 28 48.0 3
0£E» CREEK KE5ERVOIR
49051 UTAH
11EPALES 2111202
0071 FEET DEPTH CLASS 00
DATE
FRO'1
TO
75/05/12
75/08/11
75/09/19
DATE
FROM
TO
7b/u5/12
75/08/11
7b/09/l9
TIME OEPT-i
OF
DAY FEET
16 10 0000
16 10 0005
16 10 0025
16 10 0050
16 10 0071
14 40 0000
14 40 0005
14 40 0020
14 40 0045
14 40 ooao
13 35 0000
13 35 0003
13 35 0015
13 35 0030
13 35 0050
13 35 0071
TIME DEPTH
OF
DAY F£ET
16 10 0000
16 10 0005
16 10 0025
16 10 0050
16 10 0071
14 40 0000
14 40 0005
14 40 0020
14 40 0045
14 40 0080
13 35 0000
13 35 0005
13 35 OC15
13 35 0030
13 35 0050
13 35 0071
00010
«ATER
TLMP
CENT
9.0
8.6
8.1
6.1
5.4
?3.3
23. d
21.3
16. 1
12.9
18.7
Its. 7
18.3
18.3
17.5
16.6
00665
PHOS-TOT
Mu/L P
0.046
0.035
0.027
0.028
0.045
C.024
0,025
0.020
0.045
0.052
C.039
0.033
0.033
0.037
0.030
0.099
00300
00
MG/L
10.4
10.4
9.6
9.0
11.0
7.P
7.2
5.8
4.4
4.8
9.0
9.0
8.2
8.6
3.6
3.4
32217
CHLRPHYL
A
UG/L
9.3
1.3
18.7
00077 00094
TRANSP CNDuCWr
SECCHI FIELD
INCHES MICHOMHO
69 316
315
308
298
295
84 314
313
30S
244
223
72 304
302
303
308
321
338
00031
INGOT LT
REMNING
PERCENT
00400
PH
su
8.65
8.65
8.45
8.35
8.65
8.70
8.80
8.13
7.95
8.10
8.50
8.50
8.50
8.00
7.70
7.80
00410
T ALK
CAC03
MG/L
143
143
147
148
143
117
116
121
106
106
146
142
146
147
151
158
00610
NH3-N
TOTAL
Mu/L
0.030
0.030
0.100
0.120
0.030
0.020
0.020
0.030
0.020K
0.020K
0.020K
0.020K
0.020K
0.030
0.040
0.100
00625
TOT KJEL
N
MG/L
0.500
0.600
0.500
0.400
0.400
0.400
0.400
0.400
0.300
0.300
0.400
0.500
0.500
0.500
0.400
0.400
00630
N02&.N03
N-TOTAL
MG/L
0.180
0.180
0.220
0.240
0.190
0.050
0.050
0.140
0.350
0.360
0.070
0.070
0.070
0.150
0.350
0.280
00671
PHOS-DIS
0-fTriO
Mu/L P
0.011
0.010
0.013
0.011
0.006
0.004
0.00*
0.002
0.013
0.029
0.002
0.004
O.U03
0.003
0.004
0.019
K VALUE KiMOtfN TO BE
LESS THAN INDICATED
-------
STORE! RETRIEVAL DATE 76/08/12
490303
40 28 06.0 111 29 58.0 3
DEER CREEK RESERVOIR
49051 UTAH
DATE TIME DEPTH
FROM OF
TO DAY FEET
75/05/12 15 50 0000
15 50 0005
15 50 0012
75/08/11 14 20 0000
14 20 0005
14 20 0014
75/09/19 13 15 0000
13 15 0005
13 15 0018
00010
HATER
TEMP
CENT
9.5
9.3
8.5
23.2
23.8
22.3
18^8
18.3
18.2
00300 00077 00094
DO TRANSP CNDUCTVY
SECCHI FIELD
MG/L INCHES MICROMHO
9.6
9.8
9.0
8.8
9.0
8.1
10.4
9.0
9.0
42
60
36
310
306
307
333
331
330
311
305
303
11EPALES
2111202
0016 FEET DEPTH CLASS
00400
PH
SU
8.55
a. so
8.50
9.00
9.40
9.40
8.80
8.70
8.70
00*10
T ALK
CAC03
MG/L
138
136
136
114
114
126
146
146
145
00610
NH3-N
TOTAL
MG/L
0.030
0.030
0.030
0.020K
0.020K
0.020K
0.020
0.020
0.020K
00
00625
TOT KJEL
N
MG/L
0.400
0.400
0.300
0.200
0.200K
0.500
0.400
0.400
0.400
00630
N024N03
N-TOTAL
MG/L
0.190
0.200
0.200
0.020K
0.020K
0.020K
0.030
0.030
0.030
00671
PHOS-D1S
ORTHO
MG/L P
0.015
0.014
0.013
0.003
0.004
0.006
0.004
0.004
0.003
DATE
FROM
TO
75/05/12
75/0 8/11
75/09/19
TIME DEPTH
OF
DAY FEET
15 50 0000
15 50 0005
15 50 0012
14 20 0000
14 ?0 0005
14 20 0014
13 15 0000
13 15 0005
13 15 0018
00665
PHOS-TOT
MG/L P
0.052
0.045
0.048
0.042
0.045
0.038
0.050
0.050
0.051
32217
CHLRPHYL
A
JG/L
4.3
1.3
25.2
00031
INCDT LT
REMNING
PERCENT
K VALUE KNOWN TO BE
LESS THAN INDICATED
-------
APPENDIX E
TRIBUTARY AND WASTEWATER
TREATMENT PLANT DATA
-------
STORE! RETRIEVAL DATE 76/08/12
DATE TIME DEPTH
FROM OF
TO DAr FEET
74/11/10
74/13/14
75/01/11
75/02/08
75/03/08
75/04/05
75/05/03
75/05/17
75/06/07
75/06/21
75/07/12
75/08/16
75/09/13
75/10/05
13 00
10 00
09 40
10 00
09 30
09 15
10 00
09 45
10 00
10 10
08 50
12 30
09 30
4903A1
40 24 16.0 111 31 42.0 4
KKQVG KlVtK
49 7.5 ASPEN GROVE
0/DEEK CREEK RESERVOIR 150791
GAGE STATN .2 MI S OF DEER CREEK DAM
11EPALES 2111204
0000 FEET DEPTH CLASS 00
10630
!&N03
•OTAL
IG/L
0.216
0.272
0.432
0.504
C.480
0.480
0.220
0.230
0.220
0.190
0.155
0.375
0.375
0.170
00625
TOT KJEL
N
MG/L
0.600
0.600
0.800
0.200
0.600
0.350
0.350
0.150
0.450
0.450
0.250
0.300
0.500
0.300
00610
NH3-N
TOTAL
MG/L
0.230
0.220
0.180
0.072
0.056
0.090
0.040
0.125
0.050
0.030
0.035
0.030
0.035
0.040
00671
PHOS-DIS
ORTHO
MG/L P
0.025
0.02C
0.030
0.040
0.032
0.045
0.005
0.015
0.020
0.010
0.010
0.060
0.045
0.005
00665
PHOS-TOT
MG/L P
0.040
0.040
0.040
0.050
0.050
0.070
0.040
0.040
0.060
0.040
0.040
0.070
0.030
-------
STOKET HETRItVAL DATE T6/08/12
DATE TIME DEPTH N02&N03
FROM OF
TO DAY FEET
74/11/10
74/12/14
75/01/11
75/03/08
75/04/05
75/05/03
75/05/17
75/06/07
75/06/31
75/07/13
75/08/09
75/09/13
75/10/04
14 50
09 55
11 50
09 15
12 ?0
0? 45
08 45
09 35
10 00
14 45
13 00
09 40
4903A2
40 29 03.0 111 27 52.0 4
PROVO RIVER
49 7.5 CHARLESTON
T/DEEW CREEK RESERVOIR
DRT RD 8WDG i.2 MI N OF CHARLESTON
HEP ALES 2111204
OOOC FEET DEPTH CLASS 00
0630
&N03
OTAL
G/L
0.366
0.480
0.416
0.284
0.195
0.130
0.370
0.185
0.240
0.260
0.970
0.720
0.870
00625
TOT KJEL
N
MG/L
0.200
0.750
1.100
0.250
0.300
0.150
1.000
0.300
0.300
0.700
0.300
0.200
00610
NH3-N
TOTAL
MG/L
0.020
0.035
0.027
0.040
0.045
0.030
0.030
0.030
0.015
0.015
0.032
0.030
0.040
00671
PHOS-OIS
ORTHO
MG/L P
0.035
0.025
0.027
0.028
0.030
0.010
0.030
0.015
0.020
0.025
0.065
0.070
0.075
00665
PHOS-TOT
MG/L P
0.040
0.035
0.040
0.060
0.070
0.050
0.020
0.050
0.090
0.080
0.120
0.120
-------
STOHET RETRIEVAL DATE 76/os/i2
490381
40 27 30.0 111 30 40.0 4
49 7.5 ASPEN GROVE
T/DEER CREEK KESEKVOIR 150791
BNK 100 FT E OF ORT RD 6 M W OF CHRLSTON
11EPALES 2111204
0000 FEET DEPTH CLASS 00
TIME DEPTH
DATE
FROM or
TO DAY FEET
74/11/10 13 40
75/05/03 10 30
75/05/17 1<* 45
75/06/07 10 50
75/06/21 11 10
75/0 7/11 11 30
75/08/09 10 00
75/09/13 14 00
75/10/05 13 15
00630
N02&N03
N-TOTAL
MG/L
0.088
0.190
0.060
0.120
0.090
0.130
0.115
0.065
0.060
00625
TOT KJEL
N
MG/L
0.100
0.250
0.150
0.250
0.450
0.400
0.100
0.200
0.100K
00610
NH3-N
TOTAL
MG/L
0.040
0.026
0.025
0.015
0.017
0.010
0.055
0.010
0.005K
00671
PhOS-DIS
ORTHO
MG/L P
0.005
0.030
0.007
0.030
0.027
0.035
0.020
0.030
0.045
00665
PHOS-TOT
MG/L P
0.020
0.080
0.010
0.090
0.080
0.060
0.020
0.110
0.060
K VALUE KNOWN TO BE
LESS THAN INDICATED
-------
STORET RETRIEVAL DATE 75/OS/12
DATE TIME DEPTH N02*.N03
FROM OF
TO DAY FEET
74/11/10
75/01/11
75/02/08
75/03/08
75/04/Ob
75/05/03
75/05/17
75/06/07
75/06/21
75/07/12
75/08/09
75/09/13
75/10/05
14 ?0
10 10
11 30
09 55
09 10
11 ?0
10 00
09 00
09 50
10 30
09 50
13 15
16 ?5
40 29 Ift.O IH 28 00.0 «
SNiAKE CREEK
49 7,5 CHARLESTON
T/DEER CREEK RESERVOIR
fcS BKUG 1.4 MI N OF CHARLESTON
liEPALES 2111204
0000 FEET DEPTH CLASS 00
0630
'«.N03
OTAL
IG/L
0.720
0.576
0.528
0.490
0.485
0.540
0.620
1.100
0.760
0.780
1.200
1.050
0.770
0.790
00625
TOT KJEL
N
MG/L
0.300
0.700
0.500
0.6GO
l.?00
0.500
0.600
0.100
0.875
0.350
0.665
0.350
0.600
0.200
00610
NH3-*
TOTAL
MG/L
0.170
0.100
0.100
0.128
0.136
0.135
0.185
0.095
0.130
0.085
0.090
0.065
0.230
0.040
00671
PHOS-OIS
ORTHO
MG/L P
0.035
0.040
0.05S
0.072
0.068
0.060
0.110
0.100
0.050
0.040
0.045
0.040
0.045
0.040
00665
PHOS-TOT
MG/L P
0.035
0.050
0.090
0.100
0.070
0.130
0.160
0.116
0.120
0.050
0.091
0.050
0.120
0.080
-------
STORET RETRIEVAL DATE 76/08/12
DATE TIME DEPTH
FROM OF
TO DAY FEET
74/11/10
74/13/14
75/04/05
75/05/03
75/05/17
75/06/07
75/06/21
75/07/12
75/08/09
75/09/13
75/10/05
12 00
10 30
09 00
11 00
09 30
08 30
09 20
09 45
09 40
12 50
490301
40 27 40.0 ill 28 15.0 4
UANILLS CKtLK
49 7.5 CHARLESTON
T/DEER CHEEK RESERVOIR
HWY 113 BROS .1 MI S OF CHARLESTON
11EPALES 2111204
6000 FEET DEPTH CLASS 00
0630
!&N03
OTAL
IG/L
0.810
0.672
0.590
0.280
0.430
0.230
0.820
1.100
1.050
1.050
0.085
00625
TOT KJEL
N
MG/L
0.400
0.800
0.700
0.800
0.150
1.350
0.900
0.350
0.600
0.400
0.100
00610
NH3-N
TOTAL
MG/L
0.015
0.185
0.035
0.200
0.065
0.030
0.025
0.060
0.025
0.020
0.005
00671
PHOS-DIS
ORTHO
MG/L P
0.315
0.185
0.070
0.210
0.050
0.030
0.120
0.185
0.175
0.180
0.050
00665
PHOS-TOT
MG/L P
0.340
0.280
0.170
0.320
0.230
0.210
0.213
0.200
0.230
0.060
-------
STORET RETRIEVAL DATE 76/Orf/12
DATE TIME DEPTH N02&N03
FROM OF
TO DAY FEET
74/11/10
74/1a/14
75/01/11
75/03/08
75/03/08
75/04/05
75/05/03
75/05/17
75/06/07
75/06/21
75/CT/12
75/08/09
75/09/13
11 10
11 25
12 20
09 15
08 50
13 00
09 10
08 20
09 00
09 30
09 30
12 30
4903E1
40 24 17.0 111 27 52.0 4
MAIN CHANNEL
49 7.5 CHARLESTON
T/DEER CREEK RESERVOIR
P«VT RD BROG 2.2 MI N* OF WALLSBURG
11EPALES 2111204
0000 FEET DEPTH CLASS 00
0630
I&N03
OTAL
1G/L
0.384
0.576
0.576
0.520
0.624
0.610
0.315
0.280
0.145
0.280
0.210
0.095
0.220
00625
TOT KJEL
N
MG/L
0.500
1.000
0.300
0.700
1.250
0.400
0.700
0.500
0.650
0.6CO
0.700
0.600
0.900
00610
NH3-N
TOTAL
MG/L
0.015
0.045
0.030
0.040
0.080
0.025
0.060
0.050
0.020
0.020
0.050
0.030
0.050
00671
PriOS-DIS
ORTHO
MG/L P
0.030
0.035
0.035
0.040
0.048
0.030
0.035
0.063
0.040
0.035
0.070
0.045
0.060
00665
PHOS-TOT
MG/L P
0.050
0.070
0.070
0.080
0.140
0.100
0.160
0.252
0.140
0.070
0.190
0.060
0.170
-------
STORE! RETRIEVAL DATE 76/06/12
4903F1
40 30 26eO 111 26 26.0 4
SrRING CREEK
49 7.5 HEBEK CITY
T/QEER CREEK RESERVOIR 150791
HrfY 113 BROG BELOW HEBER CITY STP
HEP ALES 2111204
0000 FEET DEPTH CLASS 00
DATE
FROM
TO
74/11/10
74/12/10
75/01/11
75/02/08
75/03/08
75/04/05
75/05/03
75/05/17
75/06/07
75/06/21
75/08/09
75/09/13
75/10/05
00630 00625
TIME DEPTH N02&N03 TOT KJEL
OF N-TOTAL N
GAY FEET
12
18
10
10
10
10
10
09
10
10
13
10
15
35
00
15
00
00
14
10
05
20
30
30
MG/L
0
0
0
0
0
0
0
0
0
0
0
0
0
.650
.624
.540
.384
.232
.340
.210
.230
.480
.660
.990
.750
.550
MG/L
0.
0.
1.
1.
1.
0.
0.
2.
0.
1.
0.
0.
0.
500
600
100
000
850
950
850
000
850
050
900
900
200
00610 00671 00665
NH3-N PHOS-DIS PHOS-TOT
TOTAL ORTHO
MG/L
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
o.
0.
065
125
280
256
166
240
195
140
050
060
145
175
020
MG/L
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
P
330
210
250
208
152
200
210
115
105
115
230
280
190
MG/L P
0.370
0.300
0.400
0.320
0.280
0.335
0.320
0.210
0.220
0.190
0.280
0.460
0.220
-------
STOSET rtETRIEVAL DATE 76/OS/12
DATE TIME DEPTH N02&N03
FROM OF
TO DAY FEET
75/01/15 14 10
75/05/02 \3 45
75/05/29 10 30
75/06/09 14 55
75/07/02 13 00
75/C8/13 11 30
75/09/09 12 30
75/10/30 10 30
75/12/16 11 05
4903AA N04903AA POOOOOO
40 30 00.0 111 28 00.0 4
CLEARVIEW TROUT FARM
49 7.5 HEfaER
T/DEE* CREEK RES. 150791
PROVO RIVER
HEP ALES 2141204
0000 FEET DEPTH CLASS 00
0630
&N03
OTAL
G/L
0.080
0.150
0.150
0.150
0.100
0.100
0.125
0.100
0.125
00625
TOT KJEL
N
MG/L
.OOOK
.100
.400
0.500K
.900
.500
.000
2.750
1.300
00610
NH3-N
TOTAL
MG/L
0.050K
0.050K
0.120
0.050K
0.050K
0.025K
0.025K
0.025K
00671
PHOS-DIS
ORTHO
MG/L f»
0.050K
0.100K
0.093
0.100
0.074
0.140
0.110
0.025K
0.050
00665
PHOS-TOT
MG/L P
0.205
0.100K
0.100K
0.100
0.400
0.240
0.110
0.170
0.100K
50051
FLOW
RATE
INST MOD
2.780
2.780
3.000
3.070
3.000
3.030
3.020
3.000
3.000
50053
CONDUIT
FLOw-MGO
MONTHLY
2.800
2.800
3.000
2.760
3.000
3.100
3.100
3.100
3.100
K VALUE KNOWN TO BE
LESS THAN INDICATED
-------
DATt.
4903CA TF*903CA
40 29 00.0 111 2B 00.0 4
MIDWAY
49 7.5 HEBER
T/DEER CREEK RES.
SNAKt CREEK
11EPALES
0000 FEET DEPTH CLASS 00
P001000
jttL
F^><
TO
75/01/15
75/04/10
75/05/02
75/05/29
75/06/0'-*
75/J7/02
7b/08/U
75/09/09
75/10/31
7S/1?/1*
TIME DEPTH
OF
JAY FEET
13 10
11 30
12 10
09 30
14 15
09 30
12 30
09 15
09 00
10 00
00630
N02&N03
N-TOTAL
MG/L
2.400
4.200
4.400
S.400
5.250
4.200
4.500
5.700
6.600
2.500
00625
TOT KJEU
N
MG/L
9.000
3.6CO
5.500
6.900
5.600
10.500
10.500
6.600
3.000
5.200
00610
NH3-N
TOTAL
MG/L
O.OSOK
O.C88
0.083
0.120
O.OSOK
0.075
0.450
0.050
0.092
0.035
00671
PHOS-DIS
ORTHO
MG/L P
2.500
2.300
3.300
1.750
1.900
1.450
4.300
2.400
3.000
2.000
00665
PHOS-TOT
MG/L P
3.800
2.800
5.000
2.600
3.900
3.100
5.400
3.400
4.000
2.700
50051
FLO*
RATE
INST MGD
0.240
0.162
0.170
0.190
0.260
0.500
0.300
0.300
0.400
0.260
50053
CONDUIT
FLOX-MGO
MONTHLY
0.19*
0.180
0.180
0.250
0.370
0.300
0.300
0.400
0.250
K VALUE KNOWN TO BE
LESS THAN INDICATED
-------
STORET RETRIEVAL OATE 76/08/12
4S03CB N04903Ce)
40 29 00.0 111 28 00.0 4
MIDWAY FISrI HAT.
49 7.5 HEBER
T/OEEK CrtEEK rtES.
SNAKE CREEK
11EPALES
2141204
0000 FEET DEPTH CLASS 00
DATE
FfrOM
TO
75/01/15
75/04/10
75/05/02
75/05/29
75/06/09
75/07/02
75/08/13
75/09/09
75/10/30
75/12/16
TIME DEPTH
OF
DAY FEcT
13 20
11 35
12 30
09 10
14 00
09 40
12 45
09 30
03 50
10 00
00630
N02&N03
M-TOTAL
MG/L
0.720
0.700
0.700
0.350
0.350
0.575
0.575
0.575
0.650
0.775
006?5
TOT KJEL
N
MG/L
l.OOOK
0.500K
0.500K
1.400
0.500K
0.320
0.900
0.885
1.400
1.800
09610
NH3-N
TOTAL
MG/L
0.050K
0.050K
0.060
0.081
0.050K
0.025K
0.055
0.025K
0.025K
0.025K
00671
PHOS-OIS
ORTriO
MG/L P
0.089
0.130
0.095
0.073
0.071
0.040
0.050
0.069
0.063
0.062
00665
PHOS-TOT
MG/L P
0.100K
0.200
0.100
0.180
0.100
0.050K
0.100K
0.100K
0.280
0.100K
50051
FLUW
RATE
INST MGO
11.300
14.700
15.000
20.900
26.800
27.500
2^.300
18.600
18.500
18.500
50053
CONDUIT
FLOw-MGD
MONTHLY
11.000
12.700
17.700
28.000
23.500
22.500
22.500
K VALUE KNOWN TO HE
LESS THAN INDICATED
-------
L DATE 76/03/12
4903FA Tf^903FA P0030CO
40 30 26eO 111 26 26.0 4
HE3EK CITY
49 7.5 HEBER CITY
T/OEEW CREEK RES. 150791
SPRING C^EEK
ilEPALES 2141204
0000 FEET DEPTH CLASS 00
DATE TIME DEPTH
FROM OF
TO DAf FEET
75/01/15 13 50
75/04/10 1? 00
75/05/02 U 20
75/05/29 10 00
75/06/09 14 35
75/07/02 1? 05
75/08/13 12 00
75/09/09 10 00
75/10/30
75/12/16 10 40
00630
N02&N03
N-TOTAL"
MG/L
0.720
1.150
1.450
2.700
3.000
2.900
3.100
2.750
2.800
1.350
00625
TOT KJEL
N
MG/L
18.000
18.500
17.500
6.900
6.000
0.750
4.100
1.600
11.000
12.000
00610
NH3-N
TOTAL
MG/L
3.150
3.700
1.250
0.100
0.140
0.025K
0.095
0.025
0.375
0.100
00671
PHOS-DIS
ORifiO
MG/L P
4.300
4.500
5.300
1.050
0.860
0.790
0.740
0.690
2.200
3.200
00665
PHOS-TOT
MG/L P
6.400
5.600
7.500
1.800
1.850
0.840
1.100
1.200
3.500
4.200
50051
FLOW
RATE
INST MOD
0.800
0.420
0.500
1.500
3.990
5.500
6.500
6.500
0.400
0.800
50053
CONDUIT
FLOd-MGD
MONTHLY
1.100
0.700
0.470
1.800
1.300
6.500
b.500
0.400
0.800
K VALUE KNOWN TO BE
LESS THAN INDICATED
-------