U.S. ENVIRONMENTAL PROTECTION AGENCY
NATIONAL EUTROPHICATION SURVEY
WORKING PAPER SERIES
REPORT
ON
SHASTA LAKE
SHASTA COUNTY
CALIFORNIA
EPA REGION IX
WORKING PAPER No, 757
CORVALLIS ENVIRONMENTAL RESEARCH LABORATORY - CORVALLIS, OREGON
and
ENVIRONMENTAL MONITORING & SUPPORT LABORATORY - LAS VEGAS, NEVADA
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REPORT
ON
SHASTA LAKE
SHASTA COUNT/
CALIFORNIA
EPA REGION IX
WORKING PAPER No, 757
WITH THE COOPERATION OF THE
CALIFORNIA STATE WATER RESOURCES CONTROL BOARD
AND THE
CALIFORNIA NATIONAL GUARD
JUNE, 1973
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CONTENTS
P,ig_c
Foreword 11
List of California Study Lakes iv
Lake and Drainage Area Map v
Sections
I. Conclusions 1
II. Reservoir and Drainage Basin Characteristics 3
III. Hater Quality Summary 4
IV. Nutrient Loadings 9
V. Literature Reviewed 14
VI. Appendices 15
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11
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
V
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)]s water
quality criteria/standards review [§303(c)], clean lakes [§314(a,b)],
and water quality monitoring [§106 and §305(b)3 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 concentration (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 & Development, U.S. Environmental Protection Agency)
expresses sincere appreciation to the California State Water
Resources Control Board and the nine Regional Water Quality
Control Boards for professional involvement, to the California
National Guard for conducting the tributary sampling phase of
the Survey, and to those California wastewater treatment plant
operators who voluntarily provided effluent samples and flow
data.
The staff of the Division of Planning and Research of the
State Water Resources Control Board provided invaluable lake
documentation and counsel during the Survey, coordinated the
reviews of the preliminary reports, and provided critiques
most useful in the preparation of this Working Paper series.
Major General Glen C. Ames, the Adjutant General of Cali-
fornia, and Project Officer Second Lieutenant Terry L. Barrie,
who directed the volunteer efforts of the California National
Guardsmen, are also gratefully acknowledged for their assistance
to the Survey.
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IV
NATIONAL EUTROPHICATION SURVEY
STUDY RESERVOIRS
State of California
Name
Amador
Boca
Britton
Casitas
Crowley
Don Pedro
Elsinore
Fallen Leaf
Hennessey
Henshaw
Iron Gate
Lopez
Mary
Mendocino
Nicasio
Lower Otay
Pillsbury
Santa Margarita
Shasta
Shaver
Silver
Tahoe
Tulloch
Lower Twin
llpper Twin
County
Amador
Nevada
Shasta
Ventura
Mono
Tuolumne
Riverside
El Dorado
Napa
San Diego
Siskiyou
San Luis Obispo
Mono
Mendocino
Marin
San Diego
Lake
San Luis Obispo
Shasta
Fresno
Mono
El Dorado, Placer, CA;
Carson City, Douglas,
Washoe, NV
Calaveras, Tuolumne
Mono
Mono
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Redding1
SHASTA LAKE
Tributary Sampling Site
X Lake Sampling Site
" Sewage Treatment Facility
20 30
40 Km.
Scale
20 Hi.
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SHASTA LAKE
STORE! NO. 0621
I. CONCLUSIONS
A. Trophic Condition*:
Survey data indicate that Shasta Lake is mesotrophic. It
ranked tenth in overall trophic quality when the 24 California
lakes and reservoirs sampled in 1975 were compared using a
combination of six parameters**. Nine of the water bodies had
less median total phosphorus, 16 had less median dissolved
orthophosphorus, nine had less and five had the same median inor-
ganic nitrogen, ten had less mean chlorophyll a_, and nine had
greater mean Secchi disc transparency. No significant depression
of dissolved oxygen occurred at depths as great as 82 meters.
Survey limnologists did not observe macrophytes or surface
concentrations of algae during sampling visits.
B. Rate-Limiting Nutrient:
The results of the algal assays are not considered representa-
tive of conditions in the reservoir because of significant changes in
nutrients in the samples during shipment from the field to the
laboratory.
The reservoir data indicate nitrogen limitation at all sampling
stations and times.
* Trophic assessment is based on levels of nutrients, dissolved oxygen, and
chlorophyll a; phytoplankton kinds and numbers; and transparency (Allurn
et al., 19777.
** See Appendix A.
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C. Nutrient Controllability:
1. Point sources—The cities of Dunsmuir and Mt. Shasta
respectively contributed 0.7% and 0.6% of the total phosphorus
load to the reservoir during the sampling year. Another point
source, the City of Alturas, discharges treated wastes at a rate
of nearly 1,150 m3/day to the Pit River about 250 km upstream
from Shasta Lake (Bailey, 1977; see map, page v). However, because
of the distance and two intervening major reservoirs and several
smaller hydroelectric dams it does not seem likely that Alturas
contributes significant amounts of nutrients to the lake.
The present phosphorus loading of 3.05 g/m2/yr is nearly two
times that proposed by Vollenweider (Vollenweider and Dillon, 1974)
as a eutrophic loading (see page 13). On the basis of Survey data,
it appears the trophic quality of Shasta Lake will deteriorate
unless the phosphorus inputs can be reduced.
2. Non-point sources--Non-point sources, including direct
precipitation, contributed 98.7% of the total phosphorus load.
The Sacramento River added 10.4%; Salt Creek, 0.1%; McCloud River,
4.9%; Squaw Creek, 0.8%; the Pit River, 74.4%; and the ungaged
tributaries contributed an estimated 7.5%.
The phosphorus export rates of the Sacramento River, Salt
Creek (at C-l), McCloud River, Squaw Creek (at B-l), and the
Pit River were 34, 15, 11, 18, and 21 kg/km2/yr, respectively
(see page 12)- The somewhat higher export rate of the Sacramento
River may be due to underestimation of the known point-source loads.
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II. RESERVOIR AND DRAINAGE BASIN CHARACTERISTICS1"
A. Morphometryt"1":
1. Surface area: 119.40 kilometers2.
2. Mean depth: 46.5 meters.
3. Maximum depth: 148.4 meters.
4. Volume: 5,550.705 x 106 m3.
5. Mean hydraulic retention time: 217 days.
B. Tributary and Outlet:
(See Appendix C for flow data)
1. Tributaries -
Drainage Mean flow
Name area (km2)* (m3/sec)*
Sacramento River 1,100.7 40.950
Salt Creek 35.0 0.854
McCloud River 1,585.1 26.750
Squaw Creek 158.0 6.310'
Pit River 12,823.1 172.120
Minor tributaries &
immediate drainage - 809.1 48.396
Totals 16,511.0 295.380**
2. Outlet -
Sacramento River 16,630.4** 295.380
C. Precipitation***:
1. Year of sampling: 94.8 centimeters.
2. Mean annual: 90.2 centimeters.
t Table of metric conversions—Appendix B.
tt Dendy, 1974.
* For limits of accuracy, see Working Paper No. 175, "...Survey Methods,
1973-1976".
** Includes area of reservoir; sum of inflows adjusted to equal outflow.
*** See Working Paper No. 175.
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III. WATER QUALITY SUMMARY
Shasta Lake was sampled three times in 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 seven stations
in March, eight stations in July, and nine stations in November (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 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 73.2 meters at stations 1, 2, and 3; 42.7 meters
at station 4; 70.1 meters at station 5; 82.3 meters at station 6;
49.1 meters at station 7; 56.7 meters at station 8; and 62.8 meters at
station 9.
The sampling results are presented in full in Appendix D and are
summarized in the following table.
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PA3AMETE-1
TEMP
DI5S OXY
CNOCTVY (MCROMO)
PH (STA.MO UNITS)
TOT ALK (HG/L)
TOT P (MG/L>
OKTHO P (MG/L)
N(J2«N03 (MG/L)
AMMONIA (MG/L)
KjEL N (MG/L)
INORG N (MG/L)
TOTAL N (MG/L)
CHLS=YL A (UG/L)
SrCCHI (METERS)
A. SUMMARY OF PHYSICAL AND
1ST SAMPLING ( 3/36/75)
7 SITES
RANGE.
7.6 - 9.6
9.3 - 11.4
73. - 137.
7.5 - B.2
35. - 61.
0.017 - C.Ofrto
0.008 - 0.0^7
0.030 - 0.510
0.030 - 0.050
0.300 - 0.600
G.0<+0 ~ 0.530
0.330 - 0.710
1.3 - 5.9
1.3 - 2.6
MEAN
6.9
11. G
100.
7.9
53.
MEDIAN
9.0
11.0
105.
7,9
54.
0.023 0.022
0.019 0.01$
0.061 0.06C
0.023 0.020
0.214 0.200
0.^84 y.OtiO
0.260
3.0
0.375
3.2
l.a
l.t
CHEMICAL CHARACTERISTICS FOK SHASTA LAKE
STORET CODE 0631
RANGE
6.5 - 2S.3
6.0 - 12.0
66. - 148.
7.0 - 8.8
40. - 78.
0.006 - 0.048
0.003 - 0.041
0.030 - 0.170
0.030 - 0.060
0.300 - 0.800
0.040 - 0.200
0.220 - O.t?30
0.7 - 3.5
1.5 - 3.7
NG (
f£S
MEAN
16.2
8.5
105.
7.9
56.
0.021
0.015
0.047
0.025
0.237
0.072
0.264
1.2
2.5
7/14/75!
MEDIAN
15.1
8.3
104.
7.7
56.
0.020
0.015
0.030
0.020
0.200
0.060
0.240
0.9
2.3
3«u SAMPLING .0
93.
7.7
59.
0.021
0.013
0.020
0.020
0.20U
0.040
0.220
3.4
4.9
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B. Biological characteristics:
1. Phytoplankton -
Sampling
Date
03/26/75
Dominant
Genera
1. Stephanodiscus sp.
2. Asterionella SJD_.
3. Peri dim'urn sp.
4. Cryptomonas sp.
Total
Algal Units
per ml
1,475
413
59
30
1,977
07/14/75
1. Cryptomonas sp.
2. Synedra sp.
3. Stephanodiscus sp.
4. Chlorophytan colonies
Total
85
42
42
42
211
11/03/75
1. Melosira SJD.
2. Synedra sp.
3. Chroomonas (?)
sp_.
637
80
80
Total
797
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2. Chlorophyll a^ -
Sampling Station Chlorophyll .a
Date Number (yg/1)
03/26/75 1 1.3
2 1.6
3 3.0
4 3.3
5 2.5
6 5.9
7 4.8
8
9
07/14/75 1 0.8
2 0.7
3 0.8
4 1.0
5 0.8
6 1.4
7
8 1.4
9 2.5
11/03/75 1 2.0
2 17.0
3 29.0
4 1.9
5 2.7
6 4.0
7 2.5
8 3.8
9 3.4
C. Limiting Nutrient Study:
The results of the algal assay are not considered representa-
tive of conditions in the reservoir at the times of sampling (03/26/75
and 11/03/75) because of significant nutrient changes in the
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8
in the samples during shipment from the field to the laboratory.
The reservoir data indicate nitrogen limitation at all sampling
stations and times. Following is a tabulation of the mean inor-
ganic nitrogen/orthophosphorus ratios for each of the sampling
stations and times with the indicated limiting nutrient in
parentheses.
Station 03/26/75 07/14/75 11/03/75
1
2
3
4
5
6
7
8
9
4/1 (N)
4/1 (N)
5/1 (N)
4/1 (N)
5/1 (N)
4/1 (N)
3/1 (N)
6/1 (N)
5/1 (N)
5/1 (N)
7/1 (N)
4/1 (N)
3/1 (N)
6/1 (N)
5/1 (N)
3/1 (N)
3/1 (N)
4/1 (N)
8/1 (N)
5/1 (N)
3/1 (N)
3/1 (N)
11/1 (N)
3/1 (N)
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IV. NUTRIENT LOADINGS
(See Appendix E for data)
For the determination of nutrient loadings, the California 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 month of May 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
the California 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 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 mean concen-
trations in Nosoni Creek -at station E-l and the mean annual ZZ flow.
The operators of the Dunsmuir and Mt. Shasta wastewater treatment
plants provided monthly effluent samples and corresponding flow data;
the City of Alturas did not participate but is not considered a significant
contributor of nutrients to Lake Shasta (see page 2).
A. Waste Sources:
1. Known municipal -
Pop. Mean Flow Receiving
Name Served Treatment (m3/d) Water
Alturas* 3,130 tr. filter 1,135.5 Pit River
Dunsmuir** 2,450 stab, pond 1,732.0 Sacramento River
Mt. Shasta** 2,515 stab, pond 1,921.8 Sacramento River
2. Known industrial - None
* Anonymous, 1971.
** Treatment plant questionnaires.
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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) -
Sacramento River 37,855 10.4
Salt Creek (C-l) 540 0.1
McCloud River 17,715 4.9
Squaw Creek (B-l) 2,785 0.8
Pit River 271,400 74.4
b. Minor tributaries & immediate
drainage (non-point load) - 27,470 7.5
c. Known municipal STP's -
Alturas ?
Dunsmuir 2,535 0.7
Mt. Shasta 2,225 0.6
d. Septic tanks - Unknown ?
e. Known industrial - None
f. Direct precipitation* - 2,090 0.6
Total 364,615 100.0
2. Outputs -
Reservoir outlet - Sacramento River 316,715
3. Net annual P accumulation - 47,900 kg.
* See Working Paper No. 175.
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11
C. Annual Total Nitrogen Loading - Average Year:
1. Inputs -
kg N/ % of
Source yr total
a. Tributaries (non-point load) -
Sacramento River 2,032,775 17.8
Salt Creek (C-l) 26,445 0.2
McCloud River 687,525 6.0
Squaw Creek (B-l) 116,810 1.0
Pit River 6,323,590 55.4
b. Minor tributaries & immediate
drainage (non-point
load) - 2,083,285 18.3
c. Known municipal STP's -
Alturas ?
Dunsmuir 6,705 0.1
Mt. Shasta 6,095 0.1
d. Septic tanks - Unknown ?
e. Known industrial - None
f. Direct precipitation* - 128,905 1.1
Total 11,412,135 100.0
2. Outputs -
Reservoir outlet - Sacramento River 13,283,340
3. Net annual N loss - 1,871,205 kg.
* See Working Paper No. 175.
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12
D. Non-point Nutrient Export by Subdrainage Area:
Tributary kg P/km2/yr kg N/km2/yr
Sacramento River 34 1,847
Salt Creek (at C-l) 15 756
McCloud River 11 434
Squaw Creek (at B-l) 18 739
Pit River 21 493
E. Mean Nutrient Concentrations in Ungaged Streams:
Mean Total P Mean Total N
Tributary Cone, (mg/lj Cone, (ing/1)
Nosoni Creek 0.018 1.365
Squaw Creek (at F-l) 0.019 0.876
Salt Creek (at H-l) 0.022 1.153
Potem Creek 0.018 0.765
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13
F. Yearly Loads:
In the following table, the existing phosphorus loadings
are compared to those proposed by Vollenweider (Vollenweider
and Dillon, 1974). Essentially, his "dangerous" loading is
one at which the receiving water would become eutrophic or
remain eutrophic; his "permissible" loading is that which
would result in the receiving water remaining oligotrophic
or becoming oligotrophic if morphometry permitted. A meso-
trophic loading would be considered one between "dangerous"
and "permissible".
Note that Vollenweider's model may not be applicable to
water bodies with short hydraulic retention times.
Total Phosphorus Total Nitrogen
Total Accumulated Total Accumulated
grams/m2/yr 3.05 0.40 95.6 loss*
Vollenweider phosphorus loadings
(g/m2/yr) based on mean depth and mean
hydraulic retention time of Shasta Lake:
"Dangerous" (eutrophic loading) 1.68
"Permissible" (oligotrophic loading) 0.84
* There was an apparent loss of nitrogen during the sampling year. This
may have been due to nitrogen fixation in the reservoir, solubilization of
previously sedirnented nitrogen, recharge with nitrogen-rich ground water,
unsampled point sources discharging directly to the reservoir, or insuffi-
cient outlet sampling. Whatever the cause, a similar nitrogen loss has
occurred at Shagawa Lake, Minnesota, which has been intensively studied
by EPA's former National Eutrophication and Lake Restoration Branch (Malueg
et al., 1975).
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14
V. LITERATURE REVIEWED
Allum, M.O., R.E. Glessner, and J.H. Gakstatter, 1977. An evalua-
tion of the National Eutrophication Survey data. Working Paper
No. 900, Corvallis Env. Res. Lab., Corvallis, OR.
Anonymous, 1971. Inventory of municipal waste facilities. EPA
Publ. OWP-1, vol. 9, Wash., DC.
Bailey, Thomas E., 1977. Personal communication (reviews of pre-
liminary report). CA Water Res. Contr. Bd., Sacramento.
Dendy, William B., 1974. Personal communication (waterbody infor-
mation and morphometry). CA Water Res. Contr. Bd., Sacramento.
Malueg, Kenneth W., D. Phillips Larsen, Donald W. Schults, and
Howard T. Mercier; 1975. A six-year water, phosphorus, and
nitrogen budget for Shagawa Lake, Minnesota. Jour. Environ.
Qua!., vol. 4, no. 2, pp. 236-242.
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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15
VI. APPENDICES
APPENDIX A
LAKE RANKINGS
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LAKE DATA TO BE USED IN BANKINGS
LAKE
CODE LAKE NAME
ObOl A*ADOW RESERVOIR
0602 60CA LAKE
0603 LAKE 8PITTON
060* CASITAS RESERVOIR
0605 CPOKLEY LAKE
0606 DON PEORO RESERVOIR
0607 LAKE EUSINORE
0603 FALLEN LEAF RESERVOIR
Ob09 LAKE HENNESSEY
0610 LAKE HENSHAW
0611 IRON GATE RESERVOIR
0614 LOPEZ LAKE
0615 LAKE MARY
06it LAKE MENDOCINO
JJ617 NICASIO RESERVOIR
0618 LOWER OTAY RESERVOIR
0619 LAKE PILLSBURY
0620 SANTA MARGARITA LAKE
062i SHASTA LAKE
0622 SHAVER
0623 SILVER LAKE
0624 TULLOCK RESERVOIR
0625 UPPER TWIN LAKES
0626 LOWER TWIN LAKES
MEDIAN
TOTAL f
0.04Q
0.012
0.067
0.029
0.046
0.013
0.469
0.007
0.027
0.138
0.184
0.371
0.010
0.020
0.055
0.058
0.022
0.037
0.021
0.014
0.012
0.025
0.015
0.014
MEDIAN
INORG N
0.390
0.040
0.115
0.050
0.045
0.060
0.120
0.040
0.060
0.070
0.690
0.090
0.040
0.050
0.345
0.180
0.060
0.070
0.060
0.060
0.055
0.060
0.040
0.040
500-
MEAN SEC
408.667
372.833
44d.500
400.250
374.750
381.733
489.214
24.357
416.000
461.000
440.333
372.000
296.000
436.500
482.778
447.250
466.667
400.000
381.542
346.400
356.000
433.000
300.200
248.000
MEAN
CHLOrtA
22.383
1.700
4.811
3.192
5.800
3.564
70.572
0.786
4.525
26.783
6.217
8.658
2.550
3.100
6.633
15.933
6.389
9.122
4.087
1.700
1.800
13.878
3.340
2.900
15-
MIN oo
14.600
6.800
11.200
14.000
12.200
11.400
8.000
8.800
15.000
9.800
13.800
15.000
10.600
9.400
9.800
15.000
8.200
14.800
9.000
7.400
7.000
7.400
7.400
11.400
MEDIAN
DISS OHTnO P
0.020
0.003
0.047
0.014
0.034
0.004
0.092
O.OOS
0.012
0.073
0.124
0.343
0.002
0.008
0.013
0.013
0.008
0.014
0.015
0.004
0.003
0.009
0.004
0.003
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PERCENT OF L4KES wlT* HIGHER VALUES (NUMriE* OF LAKES WITH HIGHER VALUES)
LAKE
CODE LAKE NAME
0601 AMADOR RESERVOIR
0602 BOCA LAKE
0603 LAKE BPITTON
0604 CA5ITAS RESERVOIR
0605 CROWLEY LAKE
0606 DON PEORO RESERVOIR
0607 LAKE ELSINORE
0608 FALLEN LEAF RESERVOIR
0609 LAKE HENNESSEY
0610 LAKE HENSHAW
0611 IRON GATE RESERVOIR
061^ LOPEZ LAKE
0615 LAKE MARY
0616 LAKE MENDOCINO
0617 NICASIO RESERVOIR
0618 LOWER OTAY RESERVOIR
06i«) LAKE PILLSBURY
0620 SANTA MARGARITA LAKE
0621 SHASTA LAKE
0622 SHAVER
062J SILVER LAKE
0624 TULLOCK RESERVOIR
0625 UPPLR TWIN LAKES
0626 LOWER TWIN LAKES
MEDIAN
TOTAL P
35
69
17
43
30
83
0
100
48
13
9
4
96
65
26
22
57
39
61
78
89
52
70
74
( 8)
( 20)
( 4)
( 10)
( 7)
( 19)
( 0)
( 23)
< 11)
( 3)
( 2)
< 1)
( 22)
< 15)
( 6)
( 5)
< 13)
( 9).
( 14)
( 18)
(20)
( 12)
( 16)
( 17)
MEDIAN
INORG N
<•
98
22
74
78
54
17
B7
54
33
0
26
87
70
9
13
41
33
54
41
65
54
98
87
( 1)
( 22)
< 5)
< 17)
( 18)
( 11)
( 4)
( 19)
( 11)
( 7)
( 0)
( 6)
( 19)
( 16)
( 2)
( 3)
( 9)
( 7)
( 11)
( 9)
( 15)
< 11)
( 22)
( 19)
500-
MEAN SEC
43 1
70 i
17 i
48 I
65 i
57 i
0 i
100 i
39 i
13 I
26 I
74 I
91 1
30 I
4 I
22 i
9 l
52 *
61 1
83 1
78 1
35 1
87 1
96 1
[ 10)
t 16)
( 4)
f 11)
( 15)
( 13)
( 0)
t 23)
( 9)
I 3)
[ 6)
( 17)
I 21>
1 7)
t 1)
( 5)
I 2)
I 12)
[ 14)
U 19)
1 18)
: 8)
: 20)
I 22)
MEAN
CHLORA
9 (
91 (
48 (
7C (
43 (
61 (
0 (
100 (
52 (
4 (
39 <
26 (
83 <
74 (
30 (
13 (
35 (
22 (
57 (
96 (
87 (
17 (
65 (
78 (
2)
21)
11)
16)
10)
14)
0)
23)
12)
1)
9)
6)
19)
17)
7)
3)
8)
5)
13)
22)
20)
4)
15)
18)
15-
MIN 00
17
100
43
22
30
37
78
70
4
54
26
4
48
61
54
4
. 74
13
65
87
96
87
87
37
( 4)
( 23)
( 10)
( 5)
( 7)
( 8)
( 18)
( 16)
( 0)
( 12)
( 6)
( 0)
( 11)
( 14)
( 12)
( 0)
( 17)
( 3)
( 15)
( 19)
( 22)
( 19)
( 19)
( 8)
MEDIAN
OISS ORTHO P
26
91
17
37
22
78
9
70
52
13
4
0
100
63
46
46
63
37
30
78
91
57
78
91
( 6)
( 20)
( 4)
( 8)
( 5)
( 17)
( 2)
( 16)
( 12)
( 3)
( 1)
( 0)
( 23)
( 14)
( 10)
( 10)
( 14)
( 8)
( 7)
( 17)
( 20)
( 13)
( 17)
( 20)
INDEX
NU
134
539
164
294
268
370
104
527
249
130
104
134
505
363
169
120
279
196
328
463
506
302
485
463
-------
LAKES RANKED BY INDEX NOS.
RANK LAKE CODE LAKE NAME INDEX NO
I 0602 BOCA LAKE 539
2 0608 FALLEN LEAF RESERVOIR 527
3 0623 SILVER LAKE 506
4 0615 LAKE MARY 505
5 0625 UPPER TWIN LAKES 485
6 0626 LOWER TWIN LAKES 463
7 0622 SHAVER 463
8 0606 DON PEDRO RESERVOIR 370
9 0616 LAKE MENDOCINO 363
10 0621 SHASTA LAKE 328
11 0624 TULLOCK RESERVOIR 302
12 0604 CASITAS RESERVOIR 294
13 0619 LAKE PILLSBURY 379
14 0605 CROrfLEY LAKE 268
15 0609 LAKE HENNESSEY 249
Ib 0620 SANTA MARGARITA LAKE 196
17 0617 NICASIO RESERVOIR 169
18 0603 LAKE BRITTON 164
19 0614 LOPEZ LAKE 134
20 0601 AMADOR RESERVOIR 134
21 0610 LAKE HENSHA* 130
22 0618 LOWER OTAY RESERVOIR 120
23 0607 LAKE ELSINORE 104
24 0611 IRON GATE RESERVOIR 104
-------
APPENDIX B
CONVERSION FACTORS
-------
CONVERSION FACTORS
Hectares x 2.471 = acres
Kilometers x 0.6214 = miles
Meters x 3.281 = feet
Cubic meters x 8.107 x 10 ~^ = acre/feet
Square kilometers x 0.3861 = square miles
Cubic meters/sec x 35.315 - cubic feet/sec
Centimeters x 0.3937 = inches
Kilograms x 2.205 = pounds
Kilograms/square kilometer x 5.711 = Ibs/square mile
-------
APPENDIX C
TRIBUTARY FLOW DATA
-------
TRIBUTARY FLOW INFORMATION FOR CALIFORNIA
12/07/76
LAKE CODE 0621
SHASTA LAKE
TOTAL DRAINAGE AREA OF LAK.ECSO KM> 16630.4
SUB-DRAINAGE
TRIBUTARY
JAN
FE8
APR
MAY
NORMALIZED FLOWS(CMS)
JUN JUL AUG
SEP
OCT
NOV
DEC
MEAN
0621A1
0621A2
062IC1
0621D1
0621F 1
062101
0621ZZ
16630.4
1100.7
35.0
1585.1
158.0
1?823.1
927.2
574.83
98.26
1.671
79.57
12.2V
311. 49
94.31
438.91
60.31
2.265
39.36
16.68
216.34
127.86
212.38
69.94
1.529
46.44
11.41
263. r,6
87.51
270.43
59.75
1.642
34.83
12.20
241.83
93.46
257.68
53.24
0.510
20.93
3.71
182.64
28.42
262.78
22.14
0.218
11.92
1.61
132.81
12.36
265.61
9.23
0.113
9.71
0.85
107.60
6.54
260.80
6.54
0.074
8.44
0.54
100.24
4.16
197.65
7.65
0.057
8.55
0.42
99.68
3.27
170.75
9.88
0.173
9.43
1.27
106.19
9.73
269.86
45.59
0.425
19.20
3.20
135.07
24.51
370.95
49.84
1.671
32.85
12.29
170.18
94.31
295.38
40.95
0.854
26.75
6.31
172.12
48.39
SUMMARY
TOTAL DRAINAGE AREA OF LAKE =
SUM OF SUB-DRAINAGE AREAS =
16630.4
16629.1
TOTAL FLOW IN
TOTAL FLOW OUT
3553.99
3552.63
MEAN MONTHLY FLOWS AND GAILY FLOWS(CMS)
TRIBUTARY MONTH YEAR
0621A1
MEAN FLOW DAY
FLOW DAY
FLOW DAY
FLOW
0621A2
11
12
1
?
3
4
5
6
7
R
9
10
11
12
1
?
3
4
5
6
7
8
9
10
74
74
75
75
75
75
75
75
75
' 75
75
75
74
74
75
7b
75
75
75
75
75
75
75
75
11.582
225.40?
15.178
247.489
424.753
162.256
351.129
276.372
269.010
276.089
191. 4?2
193.970
242.675
17.387
150.646
60.598
112.418
54.65?
79.287
44. 174
12.459
8.1?7
7.164
9.826
17
15
4
2
6
3
8
13
3
7
4
17
15
4
2
6
3
8
13
3
7
4
9.430
274.390
10.336
180.661
123.745
353.960
280.317
257.400
294.495
143.380
193.687
263.630
10.477
163.955
178.113
45.873
76.739
63.430
13.366
8.495
7.221
7.023
376.614
19
97.127
-------
TRIBUTARY FLOW INFORMATION FOR
—13/07/76
LAKE CODE 06?1
SHASTA LAKE
MEAN MONTHLY FLOWS AND DAILY FLOWS
TRIBUTARY MONTH YEAR MEAN FLOW DAY
0621C1
063101
0621F1
0621G1
FLOW DAY
11
12
1
2
3
4
5
6
7
8
9
10
11
12
1
p
3
4
5
6
7
g
9
10
11
1?
1
2
3
4
5
6
7
8
9
10
11
1?
1
?
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
7b
75
75
75
75
75
75
0.184
0.26ft
0.368
2.152
4.07H
1.699
0.708
0.283
0. 161
0.099
0.074
0.108
9.741
11.100
9.996
41.3*3
65.695
32.848
35.96?
16.367
11.100
8.891
8.55?
8.608
1.359
1.98.?
2.690
15.857
30.299
12.544
5. 18?
2.124
1.189
0.736
0.538
0.793
119.214
117.23?
119.314
197.368
259.948
402.099
1427.169
1064.713
156.875
98.543
102.790
117.798
17
15
4
2
6
3
8
3
7
17
15
2
6
3
8
13
3
7
4
17
15
4
2
6
•>
a
13
3
7
4
17
15
4
2
6
3
8
3
7
4
C.144
0.153
0.153
2.35C
1.501
1.274
0.311
0.113
0.074
9.373
9.769
77.305
28.090
42.758
23.022
10.392
9.203
8.608
7.730
1.076
1.133
1.133
17.330
11.135
9.436
2.294
1.133
0.850
0.566
0.453
115.816
75.889
72.208
172.733
?30.782
1381.862
1461. l^V
80.137
67.96C
145.832
19
19
FLOW DAY
FLOrf
0.566
42.758
-------
TRIBUTARY FLOW INFORMATION FOR CALIFORNIA 12/07/76
LAKE CODE Of?l SHASTA LAKE
MEAN MONTHLY- FLO«S 4NiD DAILY FLO«fS(CMS>
TRIBUTARY MONTH YEAR MEAN FLOW OAY FLOW DAY FLOW DAY FLOW
0621ZZ ' 11 74 6.938
12 74 10.137
1 75 13.734
2 75 80.986
3 75 154.893
4 75 63.996
5 75 26.476
6 75 10.845
7 75 6.088
8 75 3.738
9 75 2.747
10 75 4.049
-------
APPENDIX D
PHYSICAL and CHEMICAL DATA
-------
STORET RETRIEVAL DATE 76/09/24
DATE
FROM
TO
75/03/26
75/07/14
75/11/03
TIME
OF
DAY
13 30
13 30
13 30
13 30
13 30
13 30
13 30
13 30
14 00
14 00
14 00
14 00
14 00
14 00
14 00
08 45
08 45
08 45
08 45
08 45
08 45
DEPTH
FEET
0000
0005
0015
0050
0100
0150
0200
0240
0000
0005
0020
0040
0080
0125
0175
0000
0005
0045
0090
0140
0175
C0010
WATER
TEMP
CENT
9.5
9.5
9.4
9.2
9.2
9.1
9.1
8. fa
24.8
24.3
?3.1
15.6
12.3
9.t
8.4
17.3
17.3
17.3
17.3
15.8
14.7
062101
40 43 10.0 122 24 53.0 3
SHASTA LAKE
06089 CALIFORNIA
140991
11EPALES
2111202
0999 FEET DEPTH CLASS
00300
00
MG/L
11.0
11.0
11.0
10.8
10.8
10.6
10.6
10.6
8.0
8.0
12.0
8.2
8.8
9.8
9.8
8.6
8.8
8.2
8.0
7.2
7.6
00077 00094
TRANSP CNOUCTVY
SECCHI FIELO
INCHES MICROMHO
96 107
106
105
106
105
107
108
109
144 97
109
109
97
90
74
68
204 87
89
89
87
77
75
00400
PH
SU
7.70
7.70
7.75
7.70
7.60
7.60
7.60
7.75
8.25
6.20
8.20
7.70
7.70
7.70
7.70
7.80
7.80
7.80
7.80
7.60
7.30
00410
T ALK
CAC03
MG/L
59
61
51
53
53
55
57
58
51
52
52
57
54
54
53
49
61
59
59
51
53
00610
NH3-N
TOTAL
MG/L
0.020
0.020K
0.020K
0.020K
0.020
0.020K
0.020
0.020K
0.030
0.020
0.020
0.030
0.020
0.030
0.020
0.020K
0.020K
0.020K
0.020K
0.020K
0.020K
00
00625
TOT KJEL
N
MG/L
0.200K
0.200K
0.200K
0.200K
0.200K
0.200K
0.200K
0.200K
0.200
0.200K
0.200K
0.200K
0.200*
0.200K
0.200K
0.200K
0.200K
0.200K
0.200K
0.200K
0.200K
00630
N026.N03
N-TOTAL
MG/L
0.060
0.060
0.070
0.070
0.070
0.070
0.070
0.090
0.040
0.020K
0.020K
0.020K
0.030
0.070
0.080
0.020K
0.020K
0.020K
0.020K
0.040
0.070
00671
PHOS-OIS
ORTHO
MG/L P
0.020K
0.021K
0.022*
0.020J
0.025K
0.021J
0.027K
0.029J
0.005
0.002K
0.002K
0.015
0.018
0.016
0.016
0.013
0.016
O.Olt
0.015
0.02b
0.02b
VALUE K.NOrfN TO BE LESS
THON INDICATED
J VALUK. KNOWN TO
TM
-------
ST3RET RETRIEVAL GATE 76/09/24
063101
40 <»3 10.0 122 24 53.0 3
SHASTA CAKE
06069 CALIFORNIA
140991
11EPALES
0999 FEET
2111202
DEPTri CLASS 00
DATE
FROM
TO
75/03/26
75/07/14
75/11/03
TIME DEPTH
OF
DAY FEET
13 30 0000
13 30 0005
13 30 0015
13 30 0050
13 30 0100
13 30 0150
13 30 C200
13 30 C240
14 00 0000
14 00 0005
14 00 0020
14 00 0040
14 00 0080
14 00 0125
14 00 0175
08 45 0000
08 45 0005
08 45 0045
Oft 45 0090
08 45 0140
08 45 0175
00665 32217
PHOS-TOT CHLRPHYL
A
MG/L P UG/L
0.019 1.3
0.020
0.019
0.022
0.019
0.021
C.024
C.031
0.010 0.8
0.007
0.006
0.024
0.0?4
0.022
0.021
0.021 2.0
0.023
0.021
0.020
0.031
0.034
00031
INCDT LT
REMNING
PERCENT
-------
STOSET RETRIEVAL DATE 76/09/24
063102
40 44 55.C 123 23 51.0 3
SHASTA LAKE
06089 CALIFORNIA
140991
11EPALES 2111202
0999 FEET OE^TH CLASS 00
DATE
FROM
TO
75/03/26
75/07/14
75/1 1/03
TIME
OF
DAY
14
14
14
14
14
14
14
14
14
14
14
14
14
14
14
14
09
09
09
09
09
09
09
40
40
40
40
40
40
40
40
30
30
30
30
30
30
30
30
15
15
15
DEPTH
FEET
ooon
OOOb
0020
0050
3100
0150
0200
0240
0000
0005
0015
0025
0045
0085
0125
0175
0000
0005
0030
15 0054
15
15
15
0090
0140
0175
00010
WATER
TEMP
CENT
9.5
9.6
9.3
9.1
9. 1
9.0
8.8
8.3
24.6
24.5
23.5
20.4
15.7
11.9
9.3
8.2
17.3
17.3
17.3
17.3
17.2
15.7
1^.9
C0300
00
MG/L
11.0
11.0
10.8
10.8
10. e
10.8
10.8
10.6
8.4
7.8
8.2
8.0
7.4
9.2
9.8
8.0
8.4
7.8
8.0
8.0
8.0
8.2
7.8
00077 00094
TRANSP CNDUCTVf
SECCH1 FIELD
INCHES M1CROMHO
102 107
110
105
108
110
133
108
137
132 123
108
106
104
102
84
81
76
240 89
89
89
89
89
77
81
00400
PH
su
7.90
7.90
7.90
7.80
7.90
8. CO
7.80
7.80
8.20
8.25
8.20
7.80
7.70
7.70
7.70
7.70
7.65
7.70
7.70
7.70
7.70
7.60
7.50
0041C
T ALK
CAC03
MG/L
54
52
51
53
54
54
55
58
53
52
52
53
62
56
55
55
55
51
53
54
56
53
30
00610
NH3-N
TOTAL
MG/L
0.020
0.020K
0.020
0.020
0.020K
0.020K
0.020K
0.020K
0.020
0.020
0.030
0.040
0.020
0.030
0.030
0.020
0.020K
0.020K
0.020K
0.020K
0.020K
0.020K
0.020K
00625
TOT KJEL
N
MG/L
0.200K
0.200K
0.200K
0.200K
0.200*
0.200K
0.200K
0.200K
0.20CK
0.200K
0.200K
0.300K
0.200K
0.200K
0.200K
0.200K
0.200K
0.200K
0.200K
0.200K
0.200K
0.200K
0.200K
00630
N02&N03
N-TOTAL
MG/L
0.060
0.060
0.060
0.060
0.060
0.060
0.080
0.100
0.020
0.020K
0.020K
0.020K
0.020K
0.030
0.070
0.080
0.020K
0.020K
0.020K
0.020K
0.020K
0.040
0.080
00671
PHOS-OIS
ORTrlO
MG/L P
0.021J
0.019J
0.027.<
0.022J
0.018J
0.022J
0.024J
0.030J
0.002K
0.002K
0.002K
0.003
0.026
0.017
0.018
0.017
0.015
0.015
0.014
0.015
0.018
0.026
0.035
KN'0"'N TO
THflN INDICATED
LE5S
VALUF KNOWN TO bE I-1
-------
STOrfET RETRIEVAL CTATE ?6/C«/24
062102
40 44 55.0 122 23 51.0 3
SHASTA LAKE
06089 CALIFORNIA
140991
11EPALES
09
-------
STORE! RETRIEVAL DATE 76/09/34
DATE
FROM
TO
75/03/26
75/07/14
75/11/03
TIME
OF
DAY
15
15
15
15
15
15
15
15
14
14
14
14
14
14
14
10
10
10
10
10
10
10
10
30
30
30
30
30
30
30
30
35
35
35
35
35
35
^5
45
45
45
45
45
45
45
«S
DEPTH
FEET
0000
OOC5
0015
0050
0100
0150
0200
0240
0000
0005
0025
0050
ulOO
0150
0220
0000
0005
0025
0060
0100
0145
0190
0230
00010
rfATER
TEMP
CENT
9.4
9.4
9.3
9.1
9.1
9.0
6.5
8.2
25.0
24.6
20.1
14. 3
9.8
7.7
6.5
17.3
17.3
17.3
17.2
17.2
15.0
13.7
11.0
062103
40 46 50.0 132 22 50.0 3
SHASTA LAKE
06069 CALIFORNIA
140991
11EPALES 2111202
0999 FEET DEPTrt CLASS 00
00300
00
MG/L
11.0
10.9
11.0
10.6
11.0
10.7
10.6
10.8
8.0
7.8
7.8
9.0
9.4
•^.8
9.8
8.2
8.0
8.2
9.2
3.0
7.7
7.6
8.0
00077 00094
TRANSP CNDUCTVr
SECCHI FIELO
INCHES MICROMHO
78 104
119
100
107
116
101
106
112
120 133
123
112
108
8C
80
73
206 110
110
108
109
86
85
92
66
00400
PH
SU
7.95
8.05
8.00
7.95
7.90
7.80
7.70
7.75
8.20
8.75
7.90
7.65
7.65
7.65
7.60
7.8C
7.80
7.80
7.80
7.70
7.55
7.45
7.40
00410
T ALK
CAC03
MG/L
53
55
54
56
57
58
57
57
53
53
52
57
47
51
47
59
60
60
62
62
56
62
37
00610
NH3-N
TOTAL
MG/L
0.020
0.020
0.020
0.020
0.020
0.020K
0.020K
0.020K
0.030
0.030
0.030
0.030
0.020
0.020
0.020K
0.020K
0.020K
0.020K
0.020K
0.020K
0.020K
0.020K
0.020K
00625
TOT KJEL
N
MG/L
0.200K
0.200K
0.200K
0.200K
0.200K
0.200K
0.200K
0.200K
0.200K
0.200K
0.200K
0.200K
0.200K
0.200K
0.200K
0.200K
0.200K
0.200K
0.200K
0.200K
0.200K
0.200K
0.200K
00630
H02&N03
M-TOTAL
MG/L
0.040
0.040
0.040
0.040
0.040
0.060
0.080
0.100
0.020
0.020K
0.020K
0.030
0.040
0.070
0.080
0.020K
0.020K
0.020K
0.020K
0.020K
0.040
0.080
0.080
00671
PHOS-OIS
04THO
MG/L P
0.009J
0.009J
0.016J
0.010J
0.010J
0.014J
0.026J
0.023J
0.005
0.004
0.010
0.027
0.016
0.018
0.015
0.012
0.012
0.012
0.013
0.014
0.021
0.024
0.013
ViLUF KNOWN TO dE LESS
THAN IvDICftTEO
KNOWN
E IN
-------
STORE! RETRIEVAL DATE 76/09/2*
DATE
FROM
TO
75/03/26
75/07/14
75/11/03
062103
40 46 50.0 122 22 50.0 3
SHA5TA LAKE
06039
140991
lltr-ALES 2111302
0999 FEET DEPTH CLASS GO
00665 32217 00031
TIME DEPTH PHOS-TOT CHLPPHYL INCDT LT
OF A REMNING
DAY FEET
15
15
15
15
15
15
15
15
14
14
14
14
14
14
14
10
10
10
10
10
10
10
10
30
30
30
30
30
30
30
30
35
35
35
35
35
35
35
45
45
45
45
45
45
45
45
0000
0005
0015
0050
0100
0150
0200
0240
0000
0005
0025
0050
0100
0150
0220
0000
0005
0025
0060
0100
0145
0190
0230
MG/L f
0.021
0.022
0.020
0.021
0.021
0.024
0.030
0 . 0 34
0.006
0.007
0.011
0.032
0.019
0.021
0.018
0.020
0.020
0.020
0.021
0.021
0.026
0.029
O.Olrf
OG/L PERCENT
3.0
0.8
29.0
-------
STORET RETRIEVAL DATE 76/09/3**
DATE
FROM
TO
75/03/27
75/07/14
75/11/03
TIME
OF
DAY
10
10
10
10
10
13
13
13
13
13
13
10
10
10
10
10
10
00
00
00
00
00
55
55
55
55
55
55
10
10
10
10
10
10
DEPTH
FEET
0000
0005
0015
0030
0055
0000
0005
0015
0050
0080
0114
0000
0005
0025
0065
0100
0140
00010
WATER
TEMP
CENT
8.8
8.4
a. a
a. 9
8.7
25.3
25.1
21.8
!<*.!
11.2
9.2
17.1
17.0
17.0
16.9
16.4
1*.9
40 51 03.0 122 23 53.0 3
SriASTA LAKE
06039 CALIFORNIA
140991
11EPALES 2111202
OObO FEET DEPTH CLASS 00
00300
DO
MG/L
11.4
11.4
11.4
11.2
9.2
7.6
8.0
7.8
8.6
8.6
8.0
8.0
8.0
fl.O
8.0
8.2
8.6
OC077
TRANSP
SECCHI
INCHES
48
60
192
00094
CNDUCTVY
FIELD
MICROMHO
80
77
77
77
73
127
125
113
79
66
72
106
106
106
103
98
101
00400
PH
SU
7.60
7.60
7.60
7.60
7.55
8.00
8.10
7.90
7.60
7.50
7.50
7.60
7.60
7.60
7.60
7.60
7.60
00410
T ALK
CAC03
MG/L
51
38
37
35
52
49
47
41
tO
41
42
65
64
64
62
58
57
00610
NH3-N
TOTAL
MG/L
0.020
0.02UK
0.020
0.020K
0.020K
0.060
0.030
0.030
0.030
0.040
0.020
0.020K
0.020K
0.020K
0.020K
0.020K
0.020K
00625
TOT KJEL
N
MG/L
0.200K
0.200*
0.200K
0.200K
0.200K
0.700
0.200K
0.200*.
0.200K
0.200K
0.200K
0.200K
0.200K
0.200K
0.200K
0.200K
0.200K
00630
N02&N03
N-TOTAL
MG/L
0.030
0.020
0.020
0.020
0.020
0.040
0.020K
0.020K
0.020K
0.040
0.050
0.020K
0.020K
0.020K
0.020K
0.020K
0.020K
00671
PriOS-OIS
ORTHO
HG/L P
0.009
0.012
0.008
0.015
0.011
0.011
O.OOb
0.006
0.007
0.016
0.011
0.006
0.006
0.006
0.004
0.003
O.OOn
K VALUE KNOWN TO BE
LtSS THAN INDICATED
-------
ET hETRIEVAL OATE 76/09/24
Ob2104
40 51 03.0 122 23 b3.0 3
SHASTA LA*£
060o9 CALIFORNIA
140991
OObO FEET DEPTH
2111202
CLASS 00
DATE
FRO1"
TO
75/03/27
75/07/li
75/11/03
00665 32217 00031
TIME DEPTH PnOS-TuT CHLSPHYL INCOT LT
OF A REMNIN&
DAY FCET
10
10
10
10
10
13
13
13
13
13
13
10
10
10
10
10
10
00
00
00
00
00
55
55
55
55
55
55
10
10
10
1C
10
10
0000
coos
0015
0030
0055
0000
OOOS
0015
0050
0060
011^
0000
0005
0025
0065
01UO
0140
MG/L C
,•
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
.Olo
.017
.022
.016
.018
.015
.009
.Ous
.010
.013
.016
.013
.014
.013
.011
.010
.018
UG/L PERCENT
3.3
1.0
1.9
-------
STORE! RETRIEVAL DATE 76/09/34
DATE
FROM
TO
75/03/27
75/07/14
75/11/OJ
00010
TIME DEPTH WATER
OF TEMP
DAY FEET
10
10
10
10
10
10
10
10
10
11
11
11
11
11
11
11
09
09
09
09
09
09
09
09
40
40
40
40
40
40
40
40
40
45
45
45
45
45
45
45
35
35
35
35
35
35
35
35
0000
0005
0015
0050
0100
0150
0180
0210
0220
0000
0005
0025
0050
0100
0150
C216
0000
0005
0035
0030
0120
0160
0195
0230
CENT
9.1
9.3
9.2
9.2
9.1
9. 1
9.0
8.8
8.7
24.1
23.8
19.4
14.6
9.7
7.8
6.7
17.2
17.2
17.2
17.2
16.0
14.3
13. 5
11.4
062105
40 47 40.0 122 17 37.0 3
SHASTA LAKE
060-9 CALIFORNIA
1^0991
11EPALES 2111202
0225 FtET DtPTh CLASS
00300
DO
MG/L
11.4
11.2
11.2
11.4
11.0
11.2
11.0
11.0
11.0
8.2
6.0
7.8
9.0
9.2
9.4
9.6
8.2
8.2
8.0
8.4
b.8
7.6
8.6
7.4
00077 00094
TRANSP CNDUCTVY
SECCHI FIELD
INCHES MICROMHO
72 103
101
102
103
107
115
119
121
121
72 132
125
106
102
88
84
82
204 109
HO
110
106
97
96
103
75
00400
PH
SU
7.90
7.90
7.90
8.00
7.95
7.90
7.80
7.80
7.75
8.30
8.30
7.95
7.70
7.70
7.70
7.60
7.80
7.80
7.75
7.70
7.55
7.50
7.50
7.40
00410
T ALK
CAC03
MG/L
49
50
50
48
49
51
54
54
54
57
56
S3
58
53
51
50
65
65
59
56
58
61
69
57
00610
NH3-N
TOTAL
MG/L
0.020
0.020K
0.020K
0.020K
0.020K
0.020K
0.040
0.030
0.030
0.020
0.020
0.030
0.030
0.030
0.020
0.020
0.020K
0.020K
0.020K
0.020K
0.020K
0.020K
0.020K
0.020K
00
00625
TOT KJEL
N
MG/L
0.200K
0.200K
0.200X
0.200K
0.200K
0.200K
0.200K
0.200K
0.200K
0.800
0.300
0.200
0.200K
0.200K
0.200K
0.200K
0.200K
0.200K
0.200K
0.200K
0.200K
0.200K
0.200K
0.200K
00630
N02kN03
N-TOTAL
MG/L
0.040
0.030
0.030
0.030
0.040
0.510
0.100
0.100
0.100
0.030
0.02C
0.020K
0.030
0.060
0.070
0.090
0.020K
0.020K
0.020K
0.020K
0.040
0.080
0.090
0.103
00671
PriOS-DIS
ORTrtO
MG/L P
0.017
0.017
0.017
0.012
0.011
0.023
0.040
0.046
0.047
0.009
O.OOJ
0.014
0.035
0.024
0.020
0.019
0.002K
0.009
0.012
0.010
0.016
0.028
0.028
0.017
K VAL
-------
STORE! RETRIEVAL DATE 7&/09/24
063105
40 47 40.0 122 17 37.0 3
SHASTA LAKE
CALIFORNIA
140991
11EPALES
0225 FEET
DtHIH
2111202
CLASS 00
00665
DATE TIME DEPTH PHOS-TOT
FROM OF
TO DAY FEET MG/L P
75/03/27
75/07/1-*
75/11/03
10
10
10
10
10
10
10
10
10
1
11
09
09
09
09
09
09
09
09
40
40
40
40
40
40
40
40
40
45
<*5
45
45
45
45
*5
35
35
35
35
35
35
35
35
0000
OOOi
0015
0050
0100
0150
0130
0210
0220
0000
0005
0025
0050
0100
0150
0216
0000
0005
0035
0080
0120
0160
0195
0230
0.021
0.018
0.019
0.019
0.021
0.030
O.OSu
0.050
0.050
0.015
0.007
0.0 ID
0.035
0.026
0.039
J.028
0.017
0.016
0.017
0.017
0.020
0.03^
0.037
0.022
32217
CHLRPHYL
A
UG/L
2.5
00031
INCDT LT
REMNING
PERCENT
0.8
2.7
-------
STORET RETRIEVAL DATE 76/09/24
OATE
FROM
TO
75/03/27
TIME OEPT-1
OK
DAY FEET
75/07/1^
75/1 1/03
09
09
09
U9
09
09
09
11
11
11
il
11
11
11
09
09
09
09
09
09
35 0000
35 0005
35 0015
35 0050
35 0090
35 0140
35 C191
10 0000
10 0005
10 0020
10 0050
10 0100
10 0150
10 0270
50 0000
50 0005
50 0040
50 0090
50 0140
50 0175
00010
WATER
TEMP
CENT
8.6
8.6
8.6
8.6
8.6
8.2
8.0
25.1
24.8
21.6
14.1
9.a
7.6
6.i>
17.4
17.4
17.4
17.3
15.6
14.6
062106
40 45 35.0 122 15 02.0 3
SHAbTA LAKE
06039 CALIFORNIA
14Q991
11EPALES
2111202
0195 FEET DEPTH CLASS
00300
DO
MG/L
11.2
10.6
11.2
11.2
11.2
11.2
11.2
8.4
8.4
8.0
8.4
9.2
9.2
9.0
8.8
8.4
7.8
7.6
7.8
8.8 .
00077 00094
TRANSP CNOUCTVY
SECCHI FIELD
INCHES MICPOMHO
60 84
82
83
83
82
87
87
108 145
134
lie
114
92
95
98
144 93
93
93
93
113
121
00400
PH
SU
8.00
8.10
8.10
8 . 20
8.15
7.95
7.90
8.50
8.50
8.00
7.70
7.60
" 7.60
7.60
7.70
7.80
7.80
7.70
7.60
7.60
00410
T ALK
CAC03
MG/L
55
55
56
54
52
57
53
58
58
68
68
60
62
64
58
58
61
59
64
68
00610
NH3-N
TOTAL
MG/L
0.040
0.020
0.020K
0.020
0.020
0.050
0.040
0.020K
0.020K
0.020K
0.020K
0.020K
0.020K
0.020K
"0.020K
0.020K
0.020K
0.020K
0.020K
0.020K
00
00625
TOT KJEL
N
MG/L
0.300
0.200K
0.200K
0.200K
0.200K
0.200
0.200K
0.200K
0.200K
0.200K
0.200K
0.200K
0.200*
0.200K
0.200*
0.200K
0.200K
0.200K
0.200K
0.200K
00630
N02ikN03
N-TOTSL
MG/L
0.040
0.030
0.020
0.020
0.020
0.080
0.080
0.020
0.020K
0.040
0.050
0.060
0.090
0.110
0.020K
0.020K
0.020K
0.030
0.080
0.080
00671
Pi-iOS-liIS
OrtTnO
MG/L P
0.016
0.010
0.009
0.010
0.011
0.035
0.031
0.005
0.005
0.037
0.041
0.027
0.029
0.023
0*012
0.012
0.012
0.016
0.028
0.023
K VALUE MNU'.'fJ TO Be
LdSS THAN INDICATED
-------
STORET RETRIEVAL DATE 76/09/24
062106
40 45 35.0 122 15 -02.0 3
SHASTA LAKE
06069 CALIFORNIA
140991
11EPALES 2111202
0195 FEET DEPTH CLASS 00
DATE
FROM
TO
75/03/27
75/07/14
75/11/03
00665 32217 00031
TIME DEPTH PHOS-TOT CHLRPHYL INCDT LT
OF A REMNING
DAY FEET
09
09
09
09
09
09
09
1
1
1
1
1
1
1
09
09
09
09
09
09
35
35
35
35
35
35
35
10
10
10
10
10
10
10
50
50
50
SO
50
50
0000
0005
0015
0050
0090
0140
0191
0000
0005
0020
0050
0100
0150
0270
0000
0005
0040
0090
0140
0175
MG/L P
0
0
0
0
0
0
0
0
0
0
0
0
c
0
0
0
0
0
0
0
.031
.02=!
.024
.025
.029
.059
.056
.012
.010
.043
.041
.032
.033
.029
.020
.021
.022
.026
.03e,
.042
UG/L PERCENT
5.9
1.4
4.0
-------
JET RETRIEVAL DATE 76/09/24
062107
40 46 40.0 122 13 30.0 3
5HASTA LAKE
060e9 CALIFORNIA
140991
11EPALES
DATE
FROM
TO
75/03/27
75/11/03
UAfE
FROM
TO
75/03/27
75/11/03
TIME DEDTH
OF
DAY FEET
09 00 0000
09 00 0005
09 00 0015
09 00 0060
09 00 0110
09 00 0160
10 20 0000
10 20 0005
10 20 0045
10 20 0090
10 20 C125
10 20 0161
TIME DEPTH
OF
OAY FEET
09 00 0000
09 00 0005
39 00 0015
0^ 00 0060
09 00 0110
09 00 0160
10 20 0000
10 20 0005
10 20 00<«5
10 20 0090
10 20 0125
10 20 0161
00010
WATER
TEMP
CENT
8.7
8.7
8.7
8.7
8.4
7.6
17.6
17.5
17.4
17.3
16.-.
14.9
00665
PHOS-TOT
MG/L P
0.031
0.027
0.026
0.035
0.037
0.066
0.020
0.023
0.021
0.022
0.077
0.036
00300
00
MG/L
11.
11.
11.
11.
11.
11.
8.
8.
8.
8.
6.
8.
32217
00077
TRANSP
SECCHI
INCHES
2 51
2
2
2
0
4
0 156
2
0
0
6
0
00031
00094
CNDUCTVY
FIELD
MICROMHO
81
82
81
82
81
76
93
93
95
93
93
97
016-
00400
Ph
su
8.20
8.20
8.20
8.10
8.00
7.90
' 7.75
7.80
7.80
7.30
7.60
7.60
2111202
* FEET DEPTH CLASS
00410
T ALK
CAC03
MG/L
54
53
51
48
47
47
66
64
58
58
61
62
00610
NH3-N
TOTAL
MG/L
0.040
0.030
0.020
0.020
0.030
0.030
0.020K
0.020K
0.020K
0.020K
0.020K
0.020K
00
00625
TOT KJEL
N
MG/L
0.600
0.200K
0.200K
0.200
0.300
0.300
0.200K
0.200K
0.200K
0.200*
0.200K
0.200K
00630
N02&N03
N-TOTAL
MG/L
0.020
0.020
0.020K
0.030
0.030
0.060
0.020K
0.020K
0.020K
0.020K
0.080
0.100
00671
PHOS-DIS
ORTHO
MG/L P
0.010
0.011
0.010
0.024
0.017
0.028
0.011
0.011
0.031
0.015
0.035
0.024
CriLRPHYL INCDT LT
A REMN1NG
UG/L PERCENT
4.
2.
P
5
< VALU£ KnOWN TO 6E
LESS THAN INDICATED
-------
STORET RETRIEVAL UATE 76/03/24
062108
<»0 47 32.0 122 10 30.0 3
SHASTA LAKE
0600* CALIFORNIA
llt'-'ALES 760109 3111202
CLASS 00
DATE
FROM
TO
75/07/14
75/11/03
TIME
OF
DAY
10
10
10
10
10
10
10
11
11
11
11
11
11
30
30
30
30
30
30
30
30
30
30
30
30
30
DEPTH
FEET
0000
0005
0015
0040
0100
0150
0186
0000
0005
0034
0065
0100
0135
00010
WATER
TEMP
CENT
25.3
25.1
21.6
15.3
9.2
7.6
7.0
17. <*
17.3
17.2
17.2
16. V
16.4
00665
DATE
FROM
TO
75/07/14
75/11/03
TIME
OF
DAY
10
10
10
10
10
10
10
30
30
30
30
30
30
30
30
30
30
30
30
30
DEPTH
FEET
OOOu
0005
0015
0040
0100
0150
0186
0000
0005
0034
0065
0100
0135
PHOS-TOT
MG/L P
0
0
0
0
0
0
0
0
C
0
0
o
0
.015
.011
.013
.034
.024
.027
.029
.017
.017
.015
.013
.012
.035
00300 00077 00094
DO TRANSP CNDUCTVY
SECCHI FIELD
MG/L
8
8
8
6
8
R
7
8
fi
8
b
8
6
3221 .
INCHES MICROMHO
.0 66
.0
.8
.8
.2
.2
.8
.4 96
.4
.4
.0
.2
.4
7 00031
148
139
121
109
104
100
97
95
97
97
97
97
101
019U l-ttl UtP
0040C 00<»10
PH T ALK
CAC03
SU
8.
a.
8.
7.
7.
7.
7.
7.
7.
7.
7.
7.
7.
40
50
30
60
60
50
Ob
8C
80
80
70
80
70
MG/L
61
60
56
61
78
64
63
63
65
65
69
63
69
CHLRPHYL INCDT LT
A
LIG/L
1
3
HEMMING
' PERCENT
.4
.8
00610 00625 00630 00671
NH3-N TOT KJEL N02&N03 PhOS-JlS
TOTAL N Nl-TOTAL ORTrtG
MG/L MG/L MG/L MG/L P
61
60
56
61
78
64
63
63
65
65
69
63
69
0.030
0.020
0.020
0.020
0.020
0.020
0.030
0.020K
0.020K
0.020K
0.020K
0.0 20K
0.020K
0.600
0.200
0.200K
0.200K
0.200K
0.200K
0.200K
0.200K
0.200K
0.200K
0.200K
0.200K
0.200K
0.040
0.020K
0.020K
0.060
0.080
0.100
0.120
0.020K
0.020K
0.020K
0.030
0.020K
0.020K
0.003
O.C02K
0.006
0.023
0.025
0.023
0.023
0.006
0.005
0.003
0.003
0.002
0.003
K VALUE M-;0«r: TO d£
LESS fntM INDICATED
-------
STORE! RETRIEVAL DATE 76/09/24
Ofc2109
40 45 05.0 122 08 J8.0 3
SHASTA LAKE
06089 CALIFORNIA
llt^ALES 760109 2111202
0210 FEET DEPTH CLASS 00
DATE
FROM
TO
75/07/1^
75/11/03
DATE
FROM
TO
75/07/14
75/11/03
TIME DEPTH
OF
DAY FEET
09 40 0000
09 40 0005
09 40 0015
09 40 0040
09 40 0100
09 40 0150
09 40 0206
11 50 0000
11 50 0005
11 50 0037
11 50 0080
11 50 0125
11 50 0175
TIME DEPTH
OF
DAY FEET
09 40 0000
09 afl 0005
09 40 0015
U9 40 0040
09 40 0100
09 aO 0150
09 40 0206
11 50 0000
11 50 OOC5
11 50 0037
11 50 0080
11 50 0125
11 50 0175
00010
rtATER
TEMP
CENT
2*. 8
24.6
22.4
15.0
9.6
7.8
7.0
17.5
17.5
17. <*
17. 4
15.1
13.7
00665
PHOS-TOT
MG/L P
0.019
0.016
C.022
0.045
0.037
G.0<+0
O.O'tH
0.022
0.021
0.020
0.023
C.038
0.052
00300
DO
MG/L
8.2
9.0
7.8
8.6
8.8
8.8
6.8
8.0
9.8
8.6
7.6
8.8
9.6
3?217
CHLRPHYL
A
UG/L
2.5
3.4
00077 00094
TRANSP CNDUCTVY
SECCHI FIELD
INCHES MICROMHO
72 142
134
121
121
92
98
96
120 95
93
93
93
91
91
00031
1NCDT LT
HEMMING
PERCENT
00400
PH
SU
ft. 80
8.80
8.40
8. 10
7.65
7.6C
7.40
7.7C
7.80
7.80
7.70
7.7o
7.80
00410
T ALK
CAC03
MG/L
60
60
61
70
60
62
64
58
59
59
59
65
67
00610
00625
NH3-N TOT
TOTAL
MG/L
0.030
0.020
0.030
0.030
0.030
0.020
0.030
1K020K
0.020K
0.020K
0.020K
0.020K
0.020K
N
KJEL
MG/L
0
0
0
0
0
0
0
0
0
0
0
0
0
.600
.200K
.300
.200K
.200K
.200
.200K
.200K
.200K
.200K
.200K
.200K
.200K
00630
N02&N03
N-TOTAL
MG/L
0.030
0.020K
0.020
C.030
0.070
0.110
0.170
0.030
0.020
0.020K
0.020
0.060
0.070
00671
PHOS-OIS
ORTHO
MG/L P
0.005
0.002
0.009
0.033
0.027
0.025
0.025
Q-.012
0.011
0.011
0.013
0.026
0.030
K
-------
APPENDIX E
TRIBUTARY and WASTEWATER
TREATMENT PLANT DATA
-------
STOPET RETRIEVAL DATE 76/09/24
0621A1
40 "3 00.0 132 25 35.0 4
SACRAMENTO RIVER
06 7.5 SHASTA DAM
0/SHA5TA LAKE
SHASTA DAM ACCESS RO BSOG .2 M BELO DAM
11EPALES 2111204
0000 FEET DEPTH CLASS 00
DATE
FROM
TO
74/11/17
74/12/15
75/01/04
75/03/02
75/04/06
75/05/03
75/05/19
75/06/OB
75/07/13
75/08/03
75/09/07
75/10/04
00630 00625
TIME DEPTH N02&N03 TOT KJEL
OF N-TOTAL N
DAY FEET
09
10
10
09
09
11
09
09
09
11
11
12
45
03
00
00
00
on
00
20
00
00
00
00
MG/L
0
0
0
0
0
0
0
0
0
0
0
.080
.088
.096
.100
.090
.130
.100
.095
.095
.090
.075
00610 00671 00665
NH3-N PHOS-DIS PHOS-TOT
TOTAL ORTHO
MG/L MG/L
0.
0.
0.
0.
1.
2.
2.
3.
0.
0.
0.
1.
750
900
900
500
100
300
400
000
500
400
800
600
0.
0.
0.
0.
0.
0.
0.
0.
c.
0.
0.
025
008
010
015
0?5
060
040
010
015
015
030
MG/L
0.
C.
0.
0.
0.
0.
0.
0.
0.
0.
p
025
025
030
025
030
030
020
020
022
020
MG/L f>
0.025
0.030
0.050
0.030
0.025
0.050
0.040
0.020
0.020
0.045
0.040
0.030
-------
RETRIEVAL DATE 75/09/24
0621A2
<»0 56 30.0 122 24 <»0.0 4
SAC^AHENTO «IV£R
Oft SHASTA CO H«Y MP
T/S-iASTA LAKE
BNr. 100 FT E 1-5
11EPALES
OOCO FEET DEPTH
1^0991
! MI S OF DELTA
2111204
CLASS 00
DATE
FROM
TO
?<./ 11/17
74/12/15
75/01/04
75/03/02
75/04/06
75/05/03
75/C5/19
75/06/08
75/07/13
75/06/03
75/09/07
75/10/04
00630 00625
TIHE DEPTH N02&N03 TOT KJEL
Of N-TOTAL N
DAY FEET
11
11
12
11
09
13
12
11
10
09
15
30
25
30
00
45
00
00
oc
30
00
30
MG/L
0
0
0
0
0
0
0
0
0
0
c
0
.056
.038
.120
.050
.025
.015
.060
.030
.025
.015
.01?
.010
MG/L
0.
1.
0.
0.
0.
0.
5.
3.
0.
2.
0.
2.
700
550
900
900
600
050K
000
300
300
eoo
200
200
00610 00671 00665
NH3-N PHOS-DIS PhOS-TOT
TOTAL ORTHO
MG/L
0.
C.
0.
c.
0.
0.
0.
0.
0.
0.
0.
0.
030
037
020
030
015
005
113
115
020
055
005
030
MG/L P
0
0
0
0
0
0
0
0
0
0
0
0
.030
.022
.025
.010
.010
.010
.005
.005
.015
.020
.030
.020
MG/L P
0.030
0.022
0.030
0.070
0.010
0.030
0.030
0.010
0.020
0.050
0.060
0.030
K VALUE KNOWN TO BE
LESS THAN INDICATED
-------
STOrtET RETRIEVAL DATE 76/09/24
DATE TIME DEPTH N02&N03
FROM OF
TO DAY FEET
74/11/17
7^/12/15
75/01/04
75/03/02
75/04/06
75/05/03
75/05/19
75/06/08
75/07/13
75/08/03
75/09/07
75/10/04
10
10
09
09
09
10
09
08
09
12
11
10
15
20
45
30
20
15
30
00
45
09
30
30
0621ol
*0 — « 35.0 132 26 05.0 4
S'JOAW CREEK
06 7.5 SHASTA DAM
T/ShASTA LAKE
IDE tfD d*DG 4 MI NW
140991
OF SHASTA DAM
0000 FEET DEPTH
2111204
CLASS 00
0630
'S.N03
OTAL
IG/L
c.o?*.
0.02*
0.04C
0.015
0.020
0.020
0.03U
0.030
0.035
0.030
0.045
0.035
OC635
TOT KJEL
N
MG/L
0.500
0.100K
0.100K
0.350
0.050K
1.600
0.700
0.900
1.700
0.100K
0.100K
0.500
00610
NH3-N
TOTAL
MO/L
0.040
0.013
C.03C
O.C05
0.045
0.055
0.050
0.060
0.055
O.C35
C.045
0.015
00671
PHOS-01S
ORThO
MG/L P
0.005
0.005K
0.005K
0.005K
0.005K
0.005K
0.005K
0.005K
0.005K
0.010
0.015
0.005
00665
PHOS-TOT
MG/L P
0.010"
0.010K
0.010r\
0.020
O.OlU:'.
0.030
0.020
O.C10K
0.010
0.01J
0.020
0.010K
K VALUE KNOWN TO BE"
LESS THAN INDICATED
-------
STORE! RETRIEVAL DATE 76/09/2**
( DATE
FROM
TO
1
7^/11/17
74/12/15
« 75/01/04
75/03/02
75/04/06
( 75/0-3/03
75/05/19
75/06/08
i 75/08/03
75/09/07
TIME 1
OF
DAY 1
12 05
11 53
11 30
12 00
10 15
1? 00
10 30
09 10
11 15
FEET
0621C1
40 51 30.0 122 16 «+5.0 4
SALT CREEK
06 SHASTA CO HWY MP
T/S^ASTA LAKE
OILMAN RD BSDG 2 Ml
lltVALES
0000 FEET DEPTH
140991
E OF SALT CRK LODGE
2111204
CLASS 00
0630
'S.N03
OTAL
G/L
o.ooe
0.010
0.056
0.040
0.015
0.010
0.025
0.0?0
0.015
0.020
00625
TOT KJEL
N
MG/L
0.500
0.650
1.200
0.700
0.950
2.800
0.400
1.100
0.500
O.POC
00610
NH3-N
TOTAL
MG/L
0.015
0.006
0.017
0.015
0.005
0.035
0.015
0.025
0.015
0.015
00671
PHOS-DIS
ORTHO
MG/L P
0.005
0.015
0.005
0.010
0.015
0.015
C.010
0.010
0.010
0.015
00665
PHOS-TOT
MG/L P
O.OlOrv
0.015
0.010K
0.020
0.015
0.040
0.010
0.030
0.020
0.030
K VftLUE KNOWN TO BE"
LESS THAN INDICATED
-------
ST3-JET .RETRIEVAL DATE 76/0
-------
STOSET RETRIEVAL DATE 7&/09/24-
0621E1
40 54 40.0 122 12 30.0 4
NOSONI CrfEEK
06 15 dOLLISOKKA MT
T/5^ASTA LAKE
SEC *0 3RDG 2.4 MI SE OF POINT MCCLOUD
11EPALES 211120^
OOCG FEET DtPTH CLASS CO
DATE TIME DEPTH
FROM OF
TO DAY FEET
74/11/17
74/12/15
75/01/04
75/03/02
75/04/06
75/05/03
75/06/08
75/07/13
75/08/03
75/09/07
75/10/04
13 20
12 40
10 15
13 00
12 00
13 15
10 30
12 15
10 00
12 30
09 30
0630
'&N03
OTAL
IG/L
0.02"
C.032
0.060
ft. 030
O.C10
0.010
0.04S
0.065
0.075
0.095
C.095
00625
TOT K^EL
N
MG/L
0.500
1.300
1.200
1.300
0.550
i.eoo
0.100K
4.300
0.800
1.000
1.100
00610
NH3-N
TOTAL
MG/L
0.025
0.022
0.020
0.015
0.005
0.025
0.005K
0.110
0.045
0.022
0.025
00671
PHOS-DIS
ORTHO
MG/L P
0.005
0.007
0.005
0.010
0.010
C.010
0.010
0.010
0.010
0.015
0.010
00665
PHOS-TOT
MG/L P
0.010*
0.010
0.010K
0.020
0.020
0.020
0.010
0.030
0.010
0.030
O.C30
K VALUE ".NOWN TO dt
LESS THAN INDICATED
-------
STORET RETRIEVAL DATE 76/09/34
( DATE
FROM
TO
t
74/11/17
74/12/15
( 75/01/04
75/03/02
75/0^/06
< 75/05/02
75/06/08
75/07/13
i 75/08/03
75/09/07
75/10/0*
TIME 1
OF
DAY 1
14 40
13 45
11 ?5
14 00
13 30
13 00
13 30
10 40
10 45
11 00
FEET
0621F1
40 52 25.0 122 07 00.0 4
SQU4* CREEK
06 15 dOLLIBOKKA MT
T/SHA5TA LAKE U0991
6rtQG ON SEC RO 7.5 MI N OF INGOT
11EPALES 2111204
0000 FEET DEPTH CLASS 00
•0630
'&N03
OTAL
IG/L
O.GO«
0.008
0.030
0.015
0.010
o.oio
0.010
0.005
0.015
0.015
0.010
00625
TOT KJEL
N
MG/L
0.400
2.600
0.500
0.150
O.R75
1.680
0.100K
0.300
1.200
0.650
1.000
00610
•NH3-N
TOTAL
MG/L
0.015
0.032
0.025
0.010
0.020
0.020
0.005K
0.140
0.022
0.015
0.025
00671
PHOS-OIS
ORTHO
MG/L P
0.015
0.010
0.005
0.015
0.015
0.010
0.015
0.010
0.010
0.010
0.010
00665
PHOS-TOT
MG/L P
0.015
0.010
0.010K
0.030
0.015
0.035
0.020
0.020
0.010
0.020
0.02C
K VALUE KNOWN TO bt
LESS THA^i IMOICATEO
-------
STORE! RETRIEVAL DATE 76/09/24
1*0 50 25.0 122 01 00.0 4
PIT rUtfE*
06 15 60LLIBOKKA MT
T/5i-
-------
STORET RETRIEVAL DATE 76/09/24
DATE TIME DEPTH N02&.N03
FROM OF
TO DAY FEET
74/11/17 13 55
74/13/15 13 30
75/01/04 11 00
75/03/02 13 30
75/04/06 13 00
75/05/03
75/08/07 10 ?5
75/09/07 11 ?0
75/10/04
062H1
40 51 55.0 122 06 22.0 4
SALT CHEEK
06 15 80LLIBOKKA MT
T/S-iASTA LAKE 140991
SEC ^D XING 2.5 Ml M SQUAW CRK Frt CON ST
11EPALES 2111204
0000 FEET DEPTH CLASS 00
0630
'&.N03
OTAL
1G/L
0.008
0.016
0.048
0.035
G.015
0.010
0.060
0.095
0.040
00625
TOT KJEL
N
MG/L
1.050
1.250
0.300
1.250
O.fi50
1.750
0.100K
2.200
0.300
OC610
NH3-N
TOTAL
MG/L
0.025
0.013
0.010
0.025
0.010
0.027
0.015
0.025
0.015
00671
PHOS-DIS
ORTHO
MG/L P
0.015
0.015
0.015
0.010
0.010
0.020
C.025
0.020
00665
PHOS-TOT
MG/L P
0.015
0.017
0.010
0.030
0.010
0.020
C.020
0.040
0.040
K VALUE KNO^N TO bt
LESS THAN INDICATED
-------
STORET RETRIEVAL DATE 76/09/24
00630
DATE TIME DEPTH N02&N03
FROM OF" N-TOTAL
TO DAY FRET MG/L
74/11/17
74/12/15
75/01/04
75/03/03
75/0^/06
75/05/03
75/06/08
75/08/07
75/0^/07
75/10/04
15
14
13
14
14
13
11
35
30
00
20
30
45
10
13 00
O.OUb
0.016
0.068
C.030
0.020
C.010
0.030
0.015
O.OtO
0.010
00625
TOT KJEL
N
MG/L
0.302
1.700
O.HOO
0.950
0.450
0.100K
0.200
1.000
1 .200
00610
NH3-N
TOTAL
MG/L
0.012
0.032
0.050
0.015
0.055
0.110
0.005K
0.060
0.030
0.015
00671
PHOS-DIS
ORTHO
MG/L P
0.010
0.010
0.010
0.015
0.010
0.015
0.015
0.015
0.015
0.010
40 51 20.0 122 02 05.0 4
POTEM CREEK
06 15 BOLLI60KKA MT
T/5*ASTA LAKE U0991
SEC *0 XING 1.3 MI N OF POTEM FALLS
11EPALES 2111204
0000 FEET OEPTh CLASS 00
00665
PHOS-TOT
MG/L P
0.010
0.020
0.030
0.010
0.020
C.020
0.015
0.020
0.020
K VALUE K-^OWN ro HE
LESS THAN INDICATED
-------
5TORET RETRIEVAL DATE 76/09/24
0621AA PU0621AA P002800
H! 11 00.0 122 16 50.0 4
DUNSMUIR
06 15 OUNSMUIR
T/L'AKE SHASTA 140992
SACRAMENTO RIVER
0000 FEET DEPTH CLASS 00
I OATE
FROM
TO
f
75/01/27
75/03/04
( 75/03/31
75/04/29
75/05/27
< 75/06/26
75/07/28
75/08/28
( 75/10/07
75/1 1/13
75/12/10
( 76/01/13
76/03/05
TIME DEPTH
OF
DAY
13
11
11
08
09
13
13
13
13
13
00
00
00
FEET
30
00
00
30
00
30
30
30
30
10
00
00
00
00630
N02S.N03
N-TOTAL
MG/L
0.080
0.080
0.080
0.050
0.050
0.075
0.025
0.050
0.075
10.500
10.500
1.650
6.000
00625
TOT KJEL
N
MG/L
18.000
5.000
4.400
12.000
9.900
15.500
12.500
14.000
20.000
4.000
3.000
3.800
l.OCOK
00610
NH3-N
TOTAL
MG/L
7.400
1.900
1.800
2.000
4.500
7.700
4.800
9.40C
5.000
1.200
0.069
0.330
0.070
00671
PHOS-DIS
ORTHO
MG/L P
4.600
1.750
1.120
2.700
4.100
4.700
4.900
5.900
5.600
".700
4.4QO
4.300
2.300
00665
PHOS-TOT
50051
FLOw
RATE
MG/L
5.
2.
1.
3.
4.
5.
6.
6.
6.
4.
5.
4.
2.
P
900
100
800
650
600
900
100
300
900
900
200
800
500
INST
0
0
0
0
0
0
0
0
0
MGD
.261
.737
.710
.452
."+72
.302
.316
.250
.300
50053
CONDUIT
FLO*/-MGO
MONTHLY
0.451
0.470
0.338
0.301
0.500
0.300
K VALUE KNOWN 70 BE
LESS THAN INDICATED
-------
STORE! SETRIEVAL DATE 76/09/24
0621AH OoeiAo P003000
41 17 00.C 122 19 15.0 4
MT. SHASTA
06 15 WEED
T/LAKE SHASTA 140192
SACriAMENTO H
DATE
FROM
TO
75/05/07
75/06/06
75/06/30
75/08/07
75/08/19
75/09/25
75/10/20
75/11/26
75/12/18
76/C1/26
76/02/17
76/03/05
76/04/02
TIME DEPTH
OF
DAY
16
14
09
09
11
10
11
10
10
11
11
21
11
00630
N02&N03
N-TOTAL
FEET
00
00
00
00
00
00
20
00
30
00
00
00
00
MG/L
0
0
0
0
0
0
0
0
0
c
0
c
0
.200
.300
.250
.450
.175
.375
.275
.350
.125
.075
.100
.2bO
.275
00625
TOT KJEL
N
MG/L
6.200
9.700
6.600
9.003
9.800
7.800
7.700
6.500
10.000
7.700
9.800
8.000
10.000
00610
NH3-N
TOTAL
MG/L
0.450
0.990
0.950
0.220
0.410
0.220
0.230
0.570
1.800
1.650
1.300
0.600
3.650
00671
PHOS-DIS
ORTHO
MG/L P
2.100
3.300
3.300
3.600
3.400
3.000
2.100
1.570
2.000
2.100
1.950
1.500
1.975
11EPALES 2141204
0000 FEET DEPTH CLASS 00
00665 50051 50053
PHOS-TOT FLOW CONDUIT
MG/L P
3.000
4.100
4.000
4.000
4.500
3.600
2.900
2.300
3.200
2.BOO
2.900
2.400
2.900
RATE
INST MGD
0.264
0.354
0.459
0.389
0.459
0.446
0.459
0.560
0.500
0.500
0.500
0.886
0.741
FLOW-MGD
MONTHLY
0
0
0
0
0
0
0
0
0
0
0
0
0
.470
.380
.400
.400
..400
.511
.539
.500
.500
.500
.500
.600
.900
------- |