2
■ OF CALIFORNIA, DAVIS
/
3 1175 01915 1839
STATE OF CALIFORNIA
The Resources Agency
epartment of Water Resources
BULLETIN No. 160-70
; mm
(JC DAVIS
WATER FOR CALIFORNIA
THE CALIFORNIA WATER PLAN
OUTLOOK IN 1970
i JUL 19 1900 li
NORMAN B. LIVERMORE, JR.
Secretary for Resources
The Resources Agency
DECEMBER 1970
RONALD REAGAN
Governor
State of California
WILLIAM R. GIANELLI
Direcfor
Department of Water Resources
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STATE OF CALIFORNIA
The Resources Agency
Department of NVa ter Resources
BULLETIN No. 160-70
WATER FOR CALIFORNIA
OUTLOOK IN 1970
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DECEMBER 1970
NORMAN B. LIVERMORE, JR.
Secretary for Resources
The Resources Agency
RONALD REAGAN
Governor
State of California
WILLIAM R. GIANELLI
Director
Department of Water Resources
FOREWORD
Over the past 30 years, California has undergone one of the
most rapid growth cycles ever experienced by a civilization.
From less than 7 million in 19^0, the State's population has
climbed to almost 20 million in 1970. Today, California is
still growing, although at a reduced pace. Recent growth trends
suggest a population of 29 million in 1990 and 45 million in
2020.
As California continues to grow, so will the demand for water —
for homes, for industry, for agriculture, for recreation and
for a quality environment for future generations. Moreover,
with increasing population will come equally increasing poten-
tial for water pollution. As we face the water problems of the
future, we must respond to emerging concepts of environmental
enhancement. Many of our past ideas must be modified to
accommodate changing environmental conditions.
Bulletin No. 16O-7O provides a summary of our current planning —
a look at what California is doing, within the framework of the
California Water Plan, about the need for water and protection
of the environment. The California Water Plan has demonstrated
that California has sufficient water supplies to meet future
needs. However, we cannot take nature's abundance for granted.
As we face the challenges of the 1970s and beyond, we must con-
tinue to assess, plan, and use our water resources in an
intelligent and thoughtful manner.
Fortunately, the projected slower growth of statewide population,
together with the additional water supplies being made available
by projects under construction or authorized, will provide a
"breathing spell" in the development of California's water
resources. This will afford additional time to consider alter-
native sources of water supply and develop policies for the
maximum protection of the environment.
William R. Gianelli, Director
Department of Water Resources
The Resources Agency
State of California
December 1, 1970
iii
TABLE OF CONTENTS
Page
FOREWORD ^^^
xj.ii
ORGANIZATION
CALIFORNIA WATER COMMISSION
XV
CHAPTER I. SUMMARY AND FINDINGS 1
Outlook in 1970 2
Organization of Report 6
CHAPTER II. AN ERA OF CHANGS 9
Emphasis on Water Quality 9
Environmental Awareness 10
Recent Environmental Legislation 11
Federal Environmental Legislation 11
National Environmental Policy Act of 19^9 H
Wild and Scenic Rivers Act (P.L. 90-5^2) 11
Water Quality Improvement Act of 1970 12
California State Environmental Legislation 12
California Protected Waterways Act 12
Assembly Select Committee on Environmental Quality .... 12
Progress in Interstate and Federal-State Water Relationships .... 14
The Water Resources Planning Act (P.L. 89-80) 1^
National Water Commission Act (P.L. 90-515) 1^
Colorado River Basin Project Act (P.L. 90-537) 15
Federal -State Framework Studies 15
Western United States Water Plan I6
Western States V/ater Council I6
Progress in 'Water Resource Development I6
Local Water Development 17
Federal Projects 18
State Water Project 19
Page
CHAPTER III. PLANNING FOR WATER RESOURCE MANAGEMENT 21
Planninf; Considerations 21
Planning Process 22
Policies J Goals and Plans 23
V/ater Resource Management Analysis Process 25
Decision and Implementation Activity 26
CHAPTER IV. WATER DEMANDS 31
Future Economic Development 31
Population 31
Industrial Development 3"
Electric Povjer Development 3°
Agricultural Developm.ent ^1
V/ater Demand ^3
Urban Water Demands ^5
Agricultural V/ater Demands ^9
Water Demands for Electric Povjer Generation 51
Recreation, Fish and VJildlife and Related Water Development .... 52
Major Policies of Federal and State
VJater Development Agencies 52
Recreation Financing 52
Fish and Wildlife Planning 53
Streamflow Maintenance for Fish and Wildlife 5^
Fish and Wildlife and Recreation V/ater Demands 55
Flood Damage Prevention 56
V/ater Quality 56
V/ater Quality and Water Use 56
Municipal and Industrial Use 57
Agricultural Use 57
Recreation 58
Fish and Aquatic Life 58
Water Quality and Water Reuse 58
Water Quality Control 60
vi
Page
CHAPTER V. POTENTIAL WATER SUPPLY SOURCES 63
Surface V/ater Development 63
Sacramento Valley Development Potential 65
North Coastal Area Development Potential 66
Ground v;ater Development 67
Availability of Ground V/ater 67
Ground V/ater Management 70
Future Ground V.'ater Use 72
Desalting 72
Department's Desalting Program 73
Federal Desalting Program 74
Current Status and Cost of Desalting Jk
Desalting in the Future 75
Water Reclamation 76
The Department's Role in Water Reclamation 76
Potential Future of Water Reclamation 77
Present Status and Use of Reclaimed V/ater 78
V/ater Reclamation Studies 80
Cost of Water Reclamation 82
Legal Requirements and Public Acceptance 82
Other Possible Sources of Water 83
Western States Water Developm.ent 83
Weather Modification 84
Watershed Management 86
Undersea Aqueduct 87
Geothermal Water Resources 88
Nonstructural Alternatives 9I
Reallocation of Water Supplies 9I
Pricing Policies gi
Increased Efficiency of Water Use 92
Mitigation of Colorado River Salinity 92
Summary 93
vii
Page
CHAPTER VI. REGIONAL WATER DEMAND-WATER SUPPLY RELATIONSHIPS .... 95
North Coastal Area 95
San Francisco Bay Area 98
Central Coastal Area 103
South Coastal Area 107
Sacramento Basin Ill
Delta-Central Sierra Area 117
San Joaquin Basin 121
Tulare Basin 125
North Lahontan Area 129
South Lahontan Area 133
Colorado Desert Area 137
Regional Water Demand -Water Supply Summary 1^2
CHAPTER VII. MEETING WATER DEMANDS THROUGH CEOTRAL VALLEY
PROJECT AND STATE WATER PROJECT FACILITIES 1^7
The Central Valley Project 1^7
The State Water Project 1^8
Operational Characteristics and Flexibilities 150
Water Supply Capabilities 151
The Role of the Peripheral Canal 153
Projected Water Demands on the Federal and State Systems 15^
Possible Central Valley Project Expansion 15^
Possible State Water Project Expansion 157
San Francisco Bay Area '. 157
Tulare Basin 158
Colorado Desert Area 158
South Coastal Area 158
Central Valley Project Water Demand-Supply Relationship .... 158
State Water Project Water Demand-Supply Relationship 159
Recreational and Environmental Accomplishments 162
Environment and the Central Valley Project l62
viii
Page
Environment and the State Water Project I63
Summary I66
CHAPTER VIII. POPULATION DISPERSAL--IMPACT ON RESOURCES
DEVELOPMENT I69
Study Criteria 170
Impact of Population Dispersal on Water Development
and the Environment 17'+
VJater Demand and Supply 17^^
Northern Model "A^' 175
Central Ftodel "B" 17t3
Southern Model "C" I76
Waste Disposal 176
Electric Power Requirements I78
Other Considerations 178
FIGURES
Number
1 Relationship of California Water Plan to Other
State Environmental and Development Policies and Plans . . 24
2 Planning for Water Resources Management
in California 29
3 United States Fertility Series 32
4 Hydrologic Study Areas of California ..... 35
5 California's Historical and Projected Population
Growth 36
6 High, Median and Low Population Project,
State of California 37
7 Generation of Electric Energy by Prime Source to
Meet Future Power Demands 39
8 Present and Projected Land Use 43
9 California's Historical and Projected Net
Irrigation Acreage, 1930-2020 44
10 California's Historical and Projected Applied
Water Demands, 1930-2020 44
11 Projected Growth of Applied Water Demands,
State of California 48
ix
FIGURES (continued)
Number Page
12 Average Annual Full Natural Runoff 6^
13 Areas of Ground Water Occurrence 68
14 Location and Relative Quantities of Municipal V.'aste
Water Discharged in Coastal Counties of California, 19^8. . 79
15 Projected Water Supplies and Net VJater Demands,
North Coastal Hydrologic Study Area 96
16 North Coastal Hydrologic Study Area 97
17 Projected V/ater Supplies and Net Water Demands,
San Francisco Bay Hydrologic Study Area 100
18 San Francisco Bay Hydrologic Study Area 101
19 Projected Water Supplies and Net Water Demands,
Central Coastal Hydrologic Study Area 10-^
20 Central Coastal Hydrolo,;;ic Study Area 105
21 Projected Water Supplies and Net Water Demands,
South Coastal Hydrologic Study Area 108
22 South Coastal Hydrologic Study Area 109
23 Projected Water Supplies and Net Water Demands,
Sacramento Basin Hydrologic Study Area 11^
24 Sacramento Basin Hydrologic Study Area 115
25 Projected V/ater Supplies and Net V/ater Demands,
Delta-Central Sierra Hydrologic Study Area Il8
26 Delta-Central Sierra Hydrologic Study Area 119
27 Projected Water Supplies and Net VJater Demands,
• San Joaquin Basin Hydrologic Study Area 122
28 San Joaquin Basin Hydrologic Study Area 123
29 Projected Water Supplies and Net Water Demands,
Tulare Basin Hydrologic Study Area 126
30 Tulare Basin Hydrologic Study Area 127
31 Projected Water Supplies and Net Water Demands,
North Lahontan Hydrologic Study Area 130
32 North Lahontan Hydrologic Study Area 131
33 Projected Water Supplies and Net Water Demands,
South Lahontan Hydrologic Study Area 13^
3^ South Lahontan Hydrologic Study Area 135
X
FIGURES (continued)
Number Page
35 Projected Water Supplies and Net Water Demands,
Colorado Desert Hydrologic Study Areas 138
36 Colorado Desert Hydrologic Study Area 139
37 Present and Projected V.'ater Demand-Water
Supply Relationships 1^3
38 Major Authorized Features of the State Water Project
and the Central Valley Project 1^9
39 The Central Valley Project, Projected Net VJater
Demands and Dependable Water Supplies I60
40 The State Viater Project, Projected Net Water
Demands and Dependable VJater Supplies I6I
41 2020 Population for Base Projection and Population
Dispersal for Models A, B and C 172
42 Population Dispersal to Nevj Urban Areas for
Models A, B and C 173
TABLES
Number Page
1 Total Population in California by Hydrologic
Study Area, I967, 1990, 2020 34
2 Present (1967) and Projected Land Use and
Irrigable Land in California by Hydrologic Study Areas . . 42
3 Estimated Urban Water Use 46
4 Present (1967) and Projected Applied and Net V/ater
Demands in California by Hydrologic Study Areas 47
5 Irrigated Agriculture, Applied Unit Water Use Values ... 49
6 Streamflow Maintenance Agreements by Hydrologic Area ... 54
7 Ground Water in California 69
8 Summary of I967 and Projected Net Water Demands and
Water Supplies by Hydrologic Study Areas l44
9 Major Features of Basic Central Valley Project and
State Water Project System 152
10 Summary of I967 and Projected Future Water Demands
on Existing Facilities of the Central Valley Project
and State Water Project 155
xi
TABLES (continued)
Number Page
11 Suiranary of Possible Future V/ater Demands Anticipated
to be Supplied by Future Facilities of the Central
Valley Project and State Water Project 156
12 Central Valley Project, Recreation-Use in I969 I65
13 Recreation-Use at State Water Project Facilities I67
ih Net Urban Water Demands in 2020 for Selected Alternative
Patterns of Future Urbanization 17^
PLATES
(in pocket at back of bulletin)
1 Water Resource Development in California
2 Irrigated, Irrigable and Urban Lands
xii
state of California
The Resources Agency
DEPARTMENT OF WATER RESOURCES
RONALD REAGAN, Governor
NORMAN B. LIVERMORE, JR., Secretary for Resources
V/ILLIAM R. GIANELLI, Director, Department of Water Resources
JOHN R. TEERINK, Deputy Director
DIVISION OF RESOURCES DEVELOPMENT
Herbert W. Greydanus Division Engineer
This bulletin was prepared under
the direction of
Albert J. Dolcini Chief, Statewide Planning Branch
by
Robert A. Williams Supervising Engineer, Water Resources
Donald K. Cole Senior Resources Economist
Assisted by
Ralph G. Allison
Marilyn J. Bennett
Edward F. Chun
Stanley W. Cummings
Eugene H. Gunderson
Roy N. Haley
Jacob W. Holderman
Jean H. Jaquith
*James C. McDade
James C. Mosley
George E. Reiner
Maurice D. Roos
Glenn B. Sawyer
Carol E. Stevenson
**Robert C. Tharratt
E. Philip Warren
Assistance was provided by the District Offices of the
Department of Water Resources
under the direction of
Gordon W. Dukleth District Engineer, Northern District
John M. Haley District Engineer, Central District
Carl L. Stetson District Engineer, San Joaquin District
James J. Doody District Engineer, Southern District
* Department of Parks and Recreation
** Department of Fish and Game
xlii
state of California
Department of V.'ater Resources
CALIFORNIA WATER COMMISSION
IRA J. CHRISMAN, Chairman, Visalia
CLAIR A. HILL, Vice Chairman, Redding
Mai Coornbs Garberville
Ray W. Ferguson Ontario
William H. Jenning? La Mesa
Clare Wm. Jones Firebaugh
William P. Moses San Pablo
Samuel B. Nelson Northridge
Ernest R. Nichols Ventura
R. Dean Thompson, Executive Officer
C. A. McCullough, Engineer
CHAPTER I. SUMMARY AND FINDINGS
This bulletin presents an up-to-
date appraisal of water demands
for various 'beneficial purposes
throughout the State for 1990 and
2020, and the potential sources of
water supplies to satisfy those
demands. It discusses accomplish-
ments in both planning and water
development implementation in the
four years since publication of
Bulletin I6O-66, the first of the
Bulletin I60 series. The Bulle-
tin 160 series reports on progress
in the implementation of the
California Water Plan and updates
certain of the concepts embodied
in that Plan.
Considerable confusion has been
evident concerning the California
Water Plan and its relationship to
the State Water Project. It is
important that the distinction
between the two be explained at
the outset to facilitate under-
standing of the information pre-
sented in this bulletin.
The California Water Plan is a
long-range planning framework for
the development of California's
water resources. The State Water
Project, currently nearing comple-
tion by the Department of Water
Resources, is a specific system
of physical facilities which will
satisfy water demands in large
areas of the State in the immediate
future. The State Water Project,
as well as all projects whether
local, state or federal, contrib-
utes toward achievement of the
objectives of the California Water
Plan as they become implemented.
This bulletin and supporting
studies deal with demands for
water and sufficiency or supplies
to satisfy those demands to 1990
and 2020, some 20 and 50 years
hence, respectively. Such projec-
tions are increasingly subject to
change with the passage of time
due to changing factors and events
that cannot be foreseen today.
Accordingly, the estimates and
projections concerning the future,
as presented in this bulletin,
represent only the magnitudes or
conditions foreseen at the present
time. It is fully recognized that
periodic revision will be necessary
in the light of additional infor-
mation and experience, and that
such revisions may well be substan-
tial--either upward or downward.
Major emphasis is placed on the
1990 projections, as these will
have considerable influence on
decisions that will be made in the
next few years. The major purpose
of the 2020 estimates is to provide
perspective for those decisions
necessary to implement plans for
water supply sources to meet demands
in the 1990s.
Findings from the studies reported
in this bulletin are set forth
under the heading "Outlook in 1970".
They are a series of concise state-
ments summarizing the information
of significant importance for which
supporting data and information are
presented in detail in the ensuing
chapters .
■1-
Outlook In 1970
In General--
• Sufficient water is developed by completed water projects, or will
be developed by those under construction, to satisfy most urban
and irrigation needs for about two decades. However, shortages in
dependable supplies presently exist in certain areas arid ccnveyence
facilities are needed to deliver developed supplies to those areas.
• The favorable status of developed water supplies affords time to
evaluate potential alternative sources of water and devote more
attention to the emerging environmental problems associated with
water conservation projects and the evolvement of definite public
policies on such problems.
• VJhereas major storage projects are not immediately needed for
water conservation, flood problems are increasing, and the control
of floods may warrant construction of storage reservoirs, which
should include conservation storage when justified.
• The quality of water supplies is generally satisfactory throughout
most of the State, with the principal exception of supplies from
the Colorado River, and care must be expressed to maintain the
good quality.
On Growth--
• The rapid growth of California's population that followed World
War II decreased sharply by the mid-1960s because of reductions
in births and migration.
• Recent trends indicate that the present population of 20 million
in California will increase to about 29 million in 1990 and
45 million in 2020, instead of 35 million and 54 million as
projected four years ago on the basis of the higher growth rates
following World War II.
• Urban land use is expected to nearly double from 2.3 million
acres at present to about 4.5 million acres in 2020 to accommodate
the projected population of 45 million.
• Irrigated acreage is expected to increase about 10 percent from
8.9 million acres at present to 9.8 million acres in 3990, onJ to
increase only an additional 4 percent to 10.2 million acres in
2020. This projected growth in acreage is less than proportional
to the projected growth of state and national requirements for
food and fiber because improved agricultural methods are
expected to produce greater yields per acre.
• Projected increases in both leisure time and extra income suggest
a rapid growth in the per capita demand for water-associated
recreation, especially near urban areas. The annual demand for
recreation is projected to increase from the current 2l8 million
visitor-days to 2.5 billion visitor-days by 2020.
-2-
« Consumption of electrical energy has generally doubled about every
10 years. This trend is expected to continue for about 20 years
and then decline slightly after 1990. Electrical-generation
requirements are expected to increase from 32,000 megawatts in
1970 to 110,000 megawatts in 1990 and Ul2,000 megawatts in 2020.
As more steam-electric powerplants are constructed, demands for
cooling water will Increase substantially.
On Needs--
• Statewide urban water demands are expected to increase from about
3.7 million acre-feet at present to 6.4 million acre-feet in 1990
and to 10.3 million acre feet in 2020. Overall per capita water
demands are expected to increase some 20 percent by 2020; however,
the growth of per capita demands in large metropolitan areas is
expected to be somewhat lower because of the projected increase in
high-rise multiple dwellings and a consequent reduction in demands
for water to irrigate lawns and gardens.
• Demands for agricultural water will generally increase; in
proportion to the growth of irrigated acreage, i.e., from
2k. h million acre-feet at present to 27.4 million acre-feet in
1990, and 28.7 million acre-feet in 2020.
• More than 80 percent of the additional electrical-generating
capacity in 1990 and 2020 is expected to be derived from fossil-
or nuclear-fueled steam plants, which requre very large amounts
of cooling water. If 50 percent of the projected increase in
generating capacity between now and 2020 is located at inland sites,
due to limited acceptability of coastal sites, about 3 million
acre-feet of cooling water will be required each year. The possible
water demands for cooling inland plants are not included in the
projected demands in this report. They could comprise one of the
largest increases in future water demands.
• Intensification of land use, resulting from the increasing
population, will require a vigorous flood control program. Local
agencies should carefully consider floodplain management in
addition to the construction of flood control facilities.
• The increasing demand for water-associated recreation will require
the development of additional water surface and shoreline,
particularly near major urban areas.
c Studies of hypothetical patterns of distribution of California's
future population indicate that, regardless of where population
centers may be located, total statewide water demands will be
essentially unchanged. Whereas the requirements for water
conservation will remain the same, new population centers would
require different patterns of water transportation facilities.
On Present Water Supplies--
« All major urban areas have adequate water supplies from existing
projects or facilities authorized or under construction to meet
water demands for the next 20 or more years.
-3-
» Adequate quantities of water are generally available for irrigation,
but in some areas, particularly in the San Joaquin Valley, ground
water is being overdrafted and in other areas, such as the Imperial
and Coachella Valleys, significant water quality problems are
emerging.
« Construction has been initiated or completed on a number of major
water supply projects during the last four years.
• The U. S. Bureau of Reclamation has completed the federal-state
San Luis Dam, Pumping Plant, and Canal and has initiated con-
struction of the Tehama-Colusa Canal, the San Felipe Division,
the San Luis drain, and the Auburn-Folsom South Unit, all
features of the Central Valley Project.
• The U. S. Army Corps of Engineers has initiated construction of
New Melones Dam on the Stanislaus River; Warm Springs Dam on
Dry Creek, a tributary of the Russian River; Martis Dam on
Martls Creek, a tributary to the Truckee River; Mojave Dam on
the Mojave River; Hidden Dam on the Chowchilla River; and
Buchanan Dam on the Fresno River.
• The State Water Project is more than 95 percent complete or
under construction, with water being delivered to the Sacra-
mento Valley, San Francisco Bay area, and the San Joaquin Valley.
Initial water delivery to Southern Calif ornia is scheduled for 1971.
• Local agencies contributed to water development by completing
or initiating construction on 35 reservoir projects. Major
projects completed were New Bullards Bar on the Yuba River (Yuba
County Water Agency), New Exchequer on the Merced River (Merced
Irrigation District), Hell Hole on the Rubicon River (Placer
County Water Agency), Lopez or Arroyo Grande Creek (San Luis
Oblsop County Flood Control and Water Conservation District),
and New Don Pedro on the Tuolumne River (City of San Francisco
and Modesto and Turlock Irrigation Districts). In addition,
the City of Los Angeles completed the second pipeline of the
Owens River Aqueduct, and several agencies in the San Joaquin
Valley have completed or are constructing major distribution
systems to deliver imported water to individual users.
On Future Water Supplies--
• The alternative sources of water considered available for meeting
future demands include surface water development by federal, state,
and local agencies; increased use of ground water in conjunction
with surface supplies; desalination; reclaimed waste water;
weather modification; and geothermal resources.
• Ground water will continue to be an important source of water. The
primary value of ground water basins lies in their use for water
storage and distribution in coordination with local and imported
surface supplies as integrated systems.
•
Desalination offers promise of a supplemental source of fresh water
particularly in California's coastal areas. However, the future
of desalted water as a major source of supply cannot be fully
evaluated until the economics of desalination have been tested
-4-
with a large-scale prototype development. The Department of Water
Resources and the U. S. Office of Saline Water are cooperating in
a program to lead to such a development by the late 1970s.
« Reclamation of waste water presents a potential source for
partial fulfillment of increasing water demands in major coastal
metropolitan areas, particularly for environmental enhancement
projects such as irrigation of recreational and agricultural
greenbelts .
• Desalination of geothermal water may eventually produce significant
quantities of fresh water and electrical energy. The Department
of Water Resources is participating in studies to determine the
feasibility of development of geothermal resources in the Imperial
Valley.
• Modification of the weather may eventually become a feasible
method for augmenting natural water supplies. The Department of
Water Resources has been participating in experiments with weather
modification since 1951-
, As a result of the projected slower growth of statewide population
as compared with projections made four years ago, future water
demands are also expected to increase more slowly. This slower
projected growth of water demands, particularly in the South
Coastal area, is expected to delay the time of need for an addi-
tional conservation facility for the State Water Project about
10 years until the mid-1990s. However, the time of need for an
additional facility could be advanced by (1) greater-than-planned
outflows of fresh water from the Sacramento-San Joaquin Delta, as
might be required by the State Water Resources Control Board;
(2) the needs of additional service areas; or (3) increased water
use in areas tributary to the Delta.
• About 1 million acre-feet of imported supplemental water will be
needed annually for the east side of the San Joaquin Valley to
offset existing large overdrafts of local ground water. The
proposed East Side Division of the Central Valley Project is a
sound engineering proposal to eliminate existing deficiencies and
to permit expansion of agricultural development. Through provisions
for stream maintenance releases, the East Side Canal has the
potential for environmentally enhancing the Sierra Nevada streams
between Dry Creek in Sacramento County and the Kern River in Kern
County. Specific plans for such releases should be developed.
• The Joint federal-state Peripheral Canal should be authorized by
Congress and constructed to enhance the environment of the
Sacramento-San Joaquin Delta and to provide good-quality water in
the Delta and for other areas of California.
• Local water agencies will continue to play an important role in
the development of California's water resources. Local agencies
are expected to develop about 20 percent of the new water supplies
required between now and 2020. They will also predominate in the
construction of distribution facilities for water delivered from
state and federal projects.
-5-
)n Special Environmental Issues--
• The rivers of California should be classified to identify their
potential for various future uses, such as scenic and wild rivers,
fisheries management, water conservation (including "lood control),
or hydroelectric power. The Department of Water Resources has
a program for characterizing the State's rivers; and the Resources
Agency is conducting a study of outstanding scenic and recreational
waterways under the California Protected Waterways Act.
• Studies of the protection and enhancement of fisheries and wildlife
habitat should be expanded to include more complete consideration
within the perspective of total resources planning and decision
processes .
• Acceptable water quality is of paramount importance in the
conservation, use, and disposal of water. The maintenance of
acceptable water quality requires an intensive effort by all
levels of government.
Organization
of Report
The text of this bulletin is pre-
sented in seven chapters. Chapter
II, "An Era of Change", discusses
changing public values and atti-
tudes toward water development
and its impact on the environment.
It also describes activities and
events since the publication of
Bulletin I6O-66 that have signif-
icant bearing on California's
water resources.
Chapter III, "Planning for Water
Resource Management", considers
environmental and social goals
in relation to water resource
planning and discusses a broad-
ened planning concept of water
resource management planning.
Chpater IV, "Water Demands",
summarizes California's water
needs on a statewide basis. It
discusses the various factors of
demand for developed supplies,
with particular emphasis on pro-
jections of population, industrial
development, irrigated agriculture,
and land use. It also discusses
the water demand-related consid-
erations of water quality, flood
control, recreation, fish and
wildlife, and other environmental
factors .
Chapter V, "Potential Water Supply
Sources", describes the various
possible sources of water that
offer potential for meeting future
water needs. However, no conclu-
sion is drawn as to the timing or
indicated priority of any particular
source .
Chapter
Water S
in some
present
for wat
each of
areas o
of exis
supplie
those d
VI, "Regio
upply Reiat
detail the
and projec
er and rela
the 11 maj
f the State
ting and de
s available
emands .
nal Water Demand-
ionships", covers
derivation of
ted future demands
ted services by
or hydrologic
and an inventory
velopable water
toward satisfying
Chapter VII, '"Meeting Water Demands
Through Central Valley Project and
State Water Project Facilities",
describes the role of the State
Water Project and the Central Valley
Project and explains the manner in
which they could be expanded and
operated to provide continuing
water service, if such service is
indicated.
-6-
Finally, Chapter VIII, "Population
Dispersal--Impact on Resources
Development", considers the impact
of possible future alternative
patterns of population distribution
on water development, use and dis-
posal, and other environmental
considerations such as sources and
transmission of electric energy,
highway transportation, and air
pollution .
It will be noted in the ensuing
chapters that the "present" is
designated as 19f-7 . This is -^he
base year chosen to reflect as
nearly as possible present (1970)
conditions, while at the same time
representing the actual development
status as determined from the most
recent land and water use surveys
which have been in progress over
the past four years. For the most
part this information, combined with
trend data and the preliminary 1970
census, has been considered repre-
sentative of present conditions.
■7-
CHAPTER II. AN ERA OF CHANGE
Since publication of Bulletin No. 3,
"The California Water Plan", in
1957j the Department has been en-
gaged in an intensive statewide
planning program to supplement and
update the California Water Plan.
This program involves: (l) peri-
odic reassessment of existing and
future demands for water and the
economic and social needs for re-
lated services such as flood con-
trol, hydroelectric power, and rec-
reational and fish and wildlife
opportunities; (2) periodic reevalu-
ation of local water resources
available to satisfy estimated
demands, and the magnitude and
timing of need for additional water
supplies that cannot be provided
from local sources; (3) evaluation
of the various alternative sources
of water supplies to meet future
demands in areas of deficiency,
including dams and reservoirs, de-
salination, reuse of reclaimed watei)
weather modification, and other
possibilities; (4) evaluation of the
need for protection and preservation
of the water resource for environ-
mental enhancement; and (5) exami-
nation of alternative water resource
management plans .
The objective of the statewide plan-
ning program is to provide a guide
to the selection of the most favor-
able management plans for
California's water resources, con-
sidering all reasonable alternative
courses of action. Evaluation of
these alternatives is premised not
only on physical and engineering
considerations but also takes into
account changing economic, social,
technological, political, and
cultural factors, as best those
factors can be foreseen. The re-
sults of the program are documented
in the Bulletin 160 series.
Since publication of the Bulletin
No. 160-66 in 1966, California has
experienced a dynamic era, not only
in the area of water project
implementation, but also in the
evolution of the broad consideration
of water resource development within
the framework of the overall envi-
ronment. Certainly, this evolution
is desirable and needed, as water is
a most valuable natural resource and
must be considered in its broadest
ramifications. The scope of plan-
ning must be broadened to encompass
fully the environmental and total
resources considerations.
Studies reported In this bulletin
indicate that estimates of future
water demand are lower than at the
time of publication of Bulletin No.
160-66, and that more time is
available to develop new water
supplies. However, concern for
environmental quality and especially
emphasis on "clean water" necessi-
tates much more effort on water
resource management. The beneficial
uses of our water resources must be
protected, and Increased effort must
be made to clean up our rivers,
lakes, estuaries, and ocean conti-
nental shelf.
Emphasis on Water Quality
Water resource management Implies
the integration of water supply with
water quality. Two major goals in
water resource management are: (l)
the management and use of the water
resources to meet the needs and
desires of the people as best those
needs can be determined; and (2) the
management of the water and related
resources of land and air to pre-
serve and enhance the resources for
indefinite use and enjoyment.
The importance of maintaining the
quality of the waters of California
has long been recognized by the
State. A major step was taken in
1967 to strengthen the water quality
control programs through the estab-
lishment of a State Water Resources
Control Board. Functions of the
-9-
five-member State Board are divided
into water rights and water quality.
The water quality functions Include
the control and prevention of water
pollution.
The State Board guides the nine
Regional Water Quality Control
Boards, enabling state policy for
water quality control to be admin-
istered regionally, within a frame-
work of statewide coordination and
policy. The Regional Boards, with
boundaries generally based on major
watershed areas, are regulatory
agencies, each gearing its work to
the specific problems of its
particular region. The Boards
formulate water quality control
plans for waters of their regions,
establish and enforce waste dis-
charge requirements, and implement
policies of the State Board.
The authority of the State Water
Resources Control Board and the
California Regional Water Quality
Control Boards was substantially
increased on January 1, 1970 when
the Porter-Cologne Water Quality
Control Act became effective. This
Act, considered the most compre-
hensive water quality control law
in the Nation, completely revises
the state water pollution and water
quality control laws and also
enables the State Water Resources
Control Board to carry out water
quality objectives through its water
rights function.
A significant element of the Act is
the provision for development by the
State Water Resources Control Board
of state policy for water quality
control and regional water quality
control plans. These policies and
plans become a part of the
California Water Plan upon sub-
mission to the Legislature.
Environmental Awareness
The recent emergence of environ-
mental awareness and concern stems
from two major considerations:
first, the obvious deterioration of
our surroundings today--air pollu-
tion, water pollution, debris of
our industrial society, urban
sprawl, loss of our natural fauna
and flora, ecological disruption,
and many other distressing aspects
of contemporary society; and
second, the predictions of what may
happen in the future as the popu-
lation pressures Increase, and the
related Impact of our expanding
technological society is Intensified.
That these problems must be solved
within a framework of comprehensive
environmental and resources policy
is becoming increasingly clear.
The real issue is the problem of
planning adequately for the use of
one resource--water--in a near
vacuum of other equally contro-
versial and interrelated problems
such as population and land use.
Planning for water use is made con-
siderably more difficult by the
absence of any firm policies and
direction in these other areas which
are the focal point of much concern.
The need for such policies is par-
ticularly manifest in water resource
development because of the long time
required for planning and
implementation.
The Department of Water Resources
recognizes the need for a compre-
hensive policy framework to provide
keener perspective with regard to
water resource development. Until
such policy is articulated by the
State, the Department must continue
its philosophy and policy of ensur-
ing that the water needs of the
people are satisfied, as best those
needs can be determined now and in
the future. The needs of people
Include not only the demand for
use, but also the need for preser-
vation of those resources. This
necessitates an awareness of the
need for planning for the mainten-
ance of a proper balance between
the preservation and protection of
water resources and the development
and use of those resources.
While there is much talk about popu-
lation control, no expectation of
some population Increase is unreal-
istic. As population Increases,
and there is every indication that
it will, water deraainds will increase
-10-
proportionately. Proper considera-
tion of environmental Issues must
be premised on the acknowledgment
that people and their related
activities will continue to need
water, no matter how the future
pattern of population growth and
distribution may occur. Therefore,
the question should not be whether
further water development should
occur, but how such development can
best be accomplished, fully taking
into account the Interrelation with
the environment and population and
land use policy, as such policy may
develop.
Recent Environmental
Legislation
With the approach of the 1970s, the
environment and environmental prob-
lems have become the watchword not
only of the public but also of the
Governor, the executive departments,
and the lawmakers. In fact, both
the State Legislature and the
Congress have declared the 1970s to
be the decade of the environment.
This is reflected at the state level
in the passage of three significant
bills, and at the federal level by
enactment or extension of important
policy statutes. While this legis-
lation is somewhat broadly based,
it will profoundly affect future
water resource development.
Federal Environmental
Legislation
Many bills concerning the environ-
ment are now pending before the
Congress, and a number of bills
dealing in various degrees with the
environment have been passed
recently. Three significant policy
enactments concerning water resource
environment are worthy of particular
note and are briefly discussed in
the following paragraphs.
National Environmental Policy Act
of 19 b9^ This Act declares national
policy to encourage productive and
enjoyable harmony between man and
his environment; to promote efforts
which will protect the environjnent
and stimulate the health and wel-
fare of man; and to enrich the
understanding of the ecological
systems and natural resources
important to the Nation. It de-
clares that the continuing policy
of the Federal Government in
cooperation with the state and
local governments and other con-
cerned public and private organi-
zations will be to use all
practicable means, including
financial and technical assistance,
to foster and promote the general
welfare .
The Act provides that all federal
agencies incorporate environment in
planning and decision-making, and
Include in every recommendation or
report a detailed statement on the
environmental impact and other con-
siderations Involved. It also re-
quires those agencies to Include
the comments of other agencies
affected. The Act also establishes
a Council on Environmental Quality
in the Executive Office of the
President. The Council assists and
advises the President and reviews
the federal agency programs and
attitudes .
Wild and Scenic Rivers Act (P.L. 90-
5^2 j. The Act, passed in 196^,
established the basic principle that
certain selected rivers of the
Nation which, with their immediate
environments, possess outstanding,
remarkable, scenic, recreation,
geologic, fish and wildlife,
historic, cultural, and other
similar values, are to be preserved
in a free -flowing condition and
protected for the benefit and the
enjoyment of present and future
generations .
The Wild and Scenic Rivers Act
established the Wild and Scenic
Rivers System, composed of eight
initial rivers, including the
Middle Ford of the Feather River,
and Identifies 27 other rivers to
be studied for possible inclusion
in the national system. In addition,
the Act also authorizes the
Secretary of the Interior to provide
-11-
technical assistance, advice, and
encouragement to the states, politi-
cal subdivisions, and private
organizations in their efforts to
establish state and local wild,
scenic, and recreation river areas.
Congress has made clear that the
task of preserving and administering
outstandingly remarkable, free-
flowing streams is not solely the
domain of the Federal Government ;
and that the states should be
encouraged to undertake as much of
the Job as is possible. To date,
12 states, including California,
have active scenic river programs
to enhance the values of free-
f lowing rivers.
Water Quality Improvement Act of
1970. The Act is aimed essentially
at strengthening federal water
pollution control authority, set-
ting up an all-inclusive federal
office to give policy guidance to
environmental quality improvement
programs, and improving effective-
ness of the federal construction
grant program in combating water
pollution.
California State Environmental
Legislation ~~~
As with the Congress, a number of
bills concerning the environment
have been passed or are under con-
sideration by the Legislature.
Three legislative acts have been
recently passed that have direct
bearing on water-related environ-
ment. Moreover, the California
Assembly Select Committee on
Environmental Quality was appointed
because of growing concern about
California's environmental problems.
California Protected Waterways Act,
This Act, passed as Chapter 127W,
Statutes of I968, has two major
aspects. First, it declares that
it is state policy to conserve
those waterways of the State
possessed of extraordinary scenic,
fishery, wildlife, or outdoor
recreation values. Second, it
requires the Resources Agency to
prepare the initial elements of a
plan and report thereon to the
Legislature by January 1971. The
Act defines waterways as "The waters
and adjacent lands of streams,
channels, lakes, reservoirs, bays,
estuaries, marshes, wetlands, and
lagoons" .
Assembly Select Committee on
Environmental Quality^ The growing
concern about California's environ-
ment prompted appointment of the
Assembly Select Committee on Environ-
mental Quality in January 1970.
This committee reviewed the major
environmental problems confronting
California and published a report
entitled "Environmental Bill of
Rights" in March of 1970. The re-
port includes 3^ recommendations
covering a wide range of recommended
state actions. Major conclusions of
the report cover population growth
and distribution, land use patterns,
need for a greatly expanded public
investment, formation of regional
planning agencies and preparation of
regional environmental protection
and enhancement plans, abatement of
pollution caused by the automobile,
and protection of resources of the
coastal zone.
Two important bills resulting from
the report were passed during the
1970 Legislative Session. They are
AB 2045, "The Environmental Quality
Act of 1970", and AB 207O, which
abolishes the existing State Office
of Planning and creates an Office of
Planning and Research in the
Governor's Office to assist the
Governor in developing and achieving
environmental goals .
AB 2045 will require state agencies
to:
1. Include a detailed statement
of specific environmental
information in any report on
any project they propose to
carry out which could signifi-
cantly affect the environment.
2. Include a detailed environ-
mental statement in the official
-12-
Californio's "Environmental Sill of Rights" is concerned with protection of resources of the coastal zone.
In .some areas, land u.se choice fta.s already been made
^ ^4^^
jv-«
.♦>..
1. .:.^'
-'it.
DPW - Drvii, lofi v< Ml
In other areas, opporlunities lor allernatlve uses still exist
state review of any proposed
federal project which could
significantly affect the
environment. (This also is
consistent with the Federal
Environmental Policy Act of
1969 requiring federal
agencies to present similar
environmental information
on their proposed projects.)
3. Request in their budgets,
funds necessary to protect
the environment from problems
caused by its activities.
4. Require from local agencies
detailed statements of
specific environmental infor-
mation prioi* to allocation
of state or federal funds for
projects which may have a
significant effect on the
environment .
Under AB 2070 the new Office of
Planning and Research will serve
the Governor and his Cabinet as
staff for long-range planning and
research, and constitute the compre-
hensive state planning agency. It
will have authority to assist in the
preparation of all environment -related
programs of state departments and
agencies. Including water develop-
ment, and to assist the Department
of Finance in preparing the annual
state budget as it relates to
environmental goals and objectives.
Progress in Interstate and
Federal-State Water
Relationships
During the nast several years a
number of steps have been taken by
California in cooperation with other
states or with the Federal Govern-
ment, and by the Federal Government,
which will have significant influ-
ence on the State's water develop-
ment. Three of the most important
federal laws enacted were : the
Water Resources Planning Act (P.L,
89-80), the National Water
Commission Act (P.L, 9O-515), and
the Colorado River Basin Project
Act (P.L. 90-537). California and
the other 10 western states have
moved toward better understanding by
their participation in the Western
States Water Council and in the
recently authorized Western United
States Water Plan Study.
The Water Resources Planning
Act (P.L. 89-80)
As stated in the preamble, this Act
is:
" ... to provide for the opti-
mum development of the Nation's
natural resources through the
coordinated planning of water
and related land resources,
through the establishment of a
water resources council and
river basins commission, and
by providing financial assis-
tance to the states in order
to increase state participation
in such planning."
Primary responsibility for imple-
mentation of this far-reaching law
rests with the Water Resources
Council, which was created by the
Act specifically for that purpose.
The Council consists of the
Secretaries of the Interior, Agri-
culture, the Army, and Health,
Education, and Welfare, and the
Chairman of the Federal Power
Commission.
The Water Resources Council is re-
quired to prepare national assess-
ments of the adequacy of supplies of
water necessary to meet each water
resource region in the United States
and the national interest therein.
The "First National Assessment" was
published by the Council in
November 1968.
National Water Commission
Act CP.L. 9O-515J
This Act, passed by the Congress in
1968, promises to be of importance
to western water development. The
Act created a seven-member National
Water Commission which is responsi-
ble for (1) review of present and
anticipated national water resource
-14-
problems; (2) consideration of
economic and social consequences of
water resource development, includ-
ing the impact of water resource
development on regional economic
growth, and on institutional
arrangements and esthetic values;
and (3) advice on specific water
matters. The Commission is also
required to consult with the Water
Resources Council, and to furnish
its reports to that body for review
and comment prior to submittal to
the President and the Congress.
The responsibilities and authority
of the Commission are very general.
During I969 it sought the views of
federal and state agencies, private
consultants, and the public in an
attempt to delineate a scope of
effort in which it could produce a
report that would give more meaning-
ful direction to the planning and
development of the Nation's water
resources. The Commission plans to
submit its final report to the
President and the Congress early in
1973.
Colorado River Basin Project
Act (P.L. 90-537)
This law was enacted in 1968 after
four years of interstate negotiations
and congressional hearings. It
authorized the Central Arizona Proj-
ect and five Upper Colorado River
Basin projects, established a devel-
opment fund, delineated principles
and priorities for operation of
Colorado River reservoirs, condi-
tionally authorized one project and
reauthorized another project in Utah,
and provided for assumption of the
Mexican Water Treaty burden by the
United States when the Colorado
River is augmented by 2.5 million
acre-feet. The Act gave existing
California, Arizona, and Nevada
Colorado River water contractors a
priority over the Central Arizona
Project whenever the annual usable
supply is less than 7.5 million acre-
feet, with California's priority
limited to 4.4 million acre-feet per
year.
The Central Arizona Project was
authorized with reference to the
1964 U. S. Supreme Court Decree
which apportions the waters of the
Lower Colorado River Basin among the
States of California, Nevada and
Arizona. Under that decree, Cali-
fornia is apportioned 4.4 million
acre -feet per year plus 50 percent
of any surplus. California agencies
have contracts with the Secretary of
the Interior for 5.362 million acre-
feet per year. It is anticipated
that California's supply in the
Colorado will be reduced when the
Central Arizona Project becomes
operational, which is expected to be
sometime during the 1980s. The
principal effect of this reduction
will be to reduce the annual deliv-
eries to the Metropolitan Viater
District of Southern California from
the present 1,212,000 acre-feet to
550,000 acre -feet. The Imperial,
Palo Verde, and Coachella Irrigation
Districts will also lose rights to
300,000 acre-feet of second-priority
water.
The Act recognizes the shortage of
water in the Colorado River Basin
and acknowledges the need for augmen-
tation of the natural water resources
of the Basin. It directs the
Secretary of the Interior to conduct
reconnaissance investigations for the
purpose of developing a general plan
to meet the future water needs of the
Western United States. However, the
Act imposes a 10-year moratorium on
studies of any plan for importation
of water into the Basin from any
other natural drainage basin lying
outside the States of Arizona,
California, Colorado, and New Mexjco
and outside of those portions of
Nevada, Utah, and Wyoming which are
in the Colorado River Basin, until
September 30, I978. The Secretary has
assigned responsibility for this study
to the Bureau of Reclamation, which
now refers to it as the "Western
United States Water Plan Study".
Federal -State Framework Studies
The Federal Government inaugurated the
Type I Framework Studies in 1966 under
the Water Resources Planning Act, with
the objective of providing compre-
hensive water planning in all regions
of the Nation. This is basically a
•15-
federal interagency program in
which the states are encouraged to
participate. The responsibility
for initiation and overall coordi-
nation has been administratively
assigned to the Water Resources
Council.
Framework Studies in the Pacific
Southwest area cover the Great
Basin, the Upper and Lower Colorado
Basins, and the California Region.
The State of California is the lead
agency for the California Region
Study, which has been in progress
since I967. All Framework Study
reports for the Region are scheduled
for completion by June 30, 1971.
The Framework Studies are being
conducted at the reconnaissance
level, with the objective of devel-
oping a framework plan to meet the
projected needs for water and re-
lated land resources through 2020.
The state agencies participating in
the California Region study are the
Departments of Water Resources,
Pish and Game, Parks and Recreation,
Navigation and Ocean Development,
Conservation, and Public Health,
and the Reclamation Board, Colorado
River Board, and State Water
Resources Control Board.
June 30, 1977. Interregional trans-
fers of water from the Northwest to
the Southwest will not be studied
in this investigation because it
will conclude before the 10-year
moratorium in P.L. 90-537 expires.
However, it was envisioned by the
Congress, in enacting P.L. 90-537,
that such transfers will be con-
sidered and a comprehensive water
plan for the entire West will be
formulated by the Secretary after
September 30, 1978.
Western States Water Council
The 33 -man Western
Council was create
governors of the 1
states lying wholl
of the Continental
purpose is to fost
cooperation among
States in planning
leading to Integra
of water resources
and other agencies
are to:
States Water
d in 1965 by the
1 contiguous
y or in part west
Divide. Its
er effective
the Western
for programs
ted development
by state, federal.
Its functions
Prepare criteria for plans
for regional development of
water resources to protect
and further state and local
interests; and
Western United States
Water Plan
The Bureau of Reclamation launched
this planning study early in 1970.
The states have been invited and
urged to participate in the investi-
gation. Insofar as possible the
study will use information to be
provided by the federal Type I
Framework Studies and any other
relevant studies for the Pacific
Northwest and the Pacific Southwest.
Progress reports are to be submit-
ted by the Secretary of the Interior
to the President, the National Water
Commission (while it is In existence),
the Water Resources Council, and
the Congress every two years . The
first report will be due on or
before June 30, I971. The study is
to terminate with a final recon-
naissance report not later than
2. Undertake continuing review
of all large-scale interstate
and interbasln plans and
projects, and advise the
governors regarding their
compatibility with the orderly
and optimum development of
the water resources of the
Western States.
Progress in
Water Resource Development
The State Water Project, the federal
Central Valley Project and other
major federal projects are widely
known, because of both the public
and governmental process of authori-
zation and the financing and indi-
vidual project scope and magnitude.
However, the extensive efforts of
local agencies, largely unhearalded,
have provided the backbone of
■16-
California's water resource devel-
opment achievement to date. Estima-
tions have been made that local
agencies have invested nearly $5
billion in surface water and ground
water projects. This estimate is
based on dollars expended over the
years, and would be substantiallj'
greater based on the value of tlie
dollar today.
It is estimated that local agencies
have expended more than $1 billion
in water conservation, conveyance,
and major distribution systems over
the past four years. The State has
invested a similar amount on the
State Water Project, and the
Federal Government has expended
about plOO million on the Central
Valley Project and other facilities.
Although state and federal construc-
tion expenditures may exceed local
agency investment in the future,
because of the increasing scope and
magnitude of interbasin projects,
state and federal water development
will continue to supplement rather
than supplant local development,
fulfill in-; onlv - \. .. ■ I.:- '\\'
local agencies are unable to
provide for. In this regard, local
agencies will play the lead role in
developin,^ distribution systems for
state and federal water facilities.
This concluding section presents a
brief description of the progress
in water development project con-
struction during the four years
since pub-licatlon of Bulletin
No. I6O-66. In this regard a map
showing existing and possible future
water development and conveyance sys-
tem.s in California is enclosed in the
jacket at the back of this bulletin
as Plate 1, entitled "Water Resource
Development in California".
Local Water Development
During the past four years local
agencies completed or initiated
construction on 35 reservoir proj-
ects. Major projects completed
were New Bullards Bar on the North
Yuba River by the Yuba County Water
Agency; New Exchequer on the Merced
New Bullards Bar Dam - North Yuba River
Yuba County Water Agency
Local projects provide the backbone lor Calilornia's water resources development
■17-
River by the Merced Irrigation
District; Hell Hole on the Rubicon
River by Placer County Water Agency;
Lopez on Arroyo Grande Creek by
San Luis Obispo County Flood Control
and Water Conservation District: and
New Don Pedro Project on the
Tuoluntne River by the City and
County of San Francisco and the
Turlock and Modesto Irrigation
Districts .
In addition, major aqueduct and
distribution systems were completed
or are in progress. The City of
Los Angeles completed the second
barrel of the Los Angeles Aqueduct
which conveys water from the Owens
River. The Metropolitan Water
District of Southern California is
constructing a major distribution
system to deliver water from the
State Water Project to member
agencies. Some $217 million in
construction was under contract on
June 30, 1969. The completed
facilities are expected to cost
about $1.4 billion.
Several major water districts in
the San Joaquin Valley have com-
pleted or are in the process of con-
structing distribution systems to
deliver imported water to individual
users. The Arvin-Edison Water
Storage District in eastern Kern
County has completed a $38 million
system for distribution of water
from the Central Valley Project.
The agencies on the west side of
the Valley are constructing similar
facilities for distribution of water
from the State Water Project, with
an aggregate expenditure of about
$40 million as of December I968.
The foregoing projects by no means
represent the total local agency
construction effort over the past
four years. But they do serve to
indicate the very important role of
the local agencies in fulfilling
California's water needs.
Federal Projects
Highlights of progress on the
Central Valley Project during the
past four years include the
completion of the J
state San Luis Dam
and San Luis Canal,
construction of the
Canal, and initiati
tion of the San Fel
Construction of the
South Unit (authori
the San Luis drain
in progress .
oint federal -
and Pumping Plant
initiation of
Tehama-Colusa
on of construc-
ipe Division.
Auburn-Folsom
zed in I965) and
is also currently
Central Valley Project deliveries
have increased 50 percent over the
past four years, reaching 60 percent
of the estimated total area contem-
plated under the presently autho-
rized project. Water deliveries in
1969 totalled 4.9 million acre-feet
as compared to 3.6 million acre-feet
in 1965. Installed hydroelectric
capacity also increased 50 percent,
currently exceeding 1,500,000
kilowatts. This represents nearly
85 percent of the presently autho-
rized total capacity.
Other noteworthy construction accom-
plishments by the Bureau of Recla-
mation include completion of
Stampede Reservoir on Little Truckee
River and first power transmission
to the Central Valley Project over
the Pacific Northwest-Pacific
Southwest intertie .
The Corps of Engineers continued its
construction program to provide for
navigation, beach erosion and flood
control projects. The Corps began
construction on six reservoir proj-
ects: New Melones on the Stanislaus
River, Warm Springs in the Russian
River Basin, Martis on the Truckee
River, Mojave on the Mojave River,
Hidden on the Fresno River, and
Buchanan on the Chowchilla River.
The Flood Control Act of I966 autho-
rized Marysville and Knights Valley
Reservoir Projects on the Yuba
River and in the Russian River Basin,
respectively, and the Flood Control
Act of 1968 authorized Butler Valley
Reservoir Project on the Mad River
in Humboldt County.
-18-
state Water Project
Notable progress has been made since
1966 toward completion of the State
Water Project. Oroville Dam has
been in operation for over three
years and has performed very suc-
cessfully its multi-purpose duties
of flood control, conservation,
power generation, and recreation.
In fact, Oroville Reservoir not
only completely filled during its
first year of full operation, but
also performed adm.irably in con-
trolling the substantial floodflows
during January and February of I969
and January of 1970.
The first phase of the North Bay
Aqueduct was completed early in
1968. Del Valle Dam on the South
Bay Aqueduct was completed in 1968
and Lake Del Valle was full by the
spring of I969.
The favorable water conditions
during the spring of I969 enabled
the complete filling of San Luis
Reservoir, the key facility of the
San Luis features which were com-
pleted in 1968.
Deliveries of project water to con-
tracting agencies in the San Joaquin
Valley began in I968, and a total
of nearly 200,000 acre-feet of water
was delivered to nine water service
agencies along the west side of the
Valley in Kings and Kern Counties in
both 1968 and I969. An estimated
300,000 acre-feet was delivered in
1970. Of the 75,000 acres currently
irrigated from project deliveries,
only 12,000 acres had previously
been irrigated.
As of December 1970 the California
Aqueduct was operational from
Clifton Court Forebay at the souther-
ly edge of the Delta to Wind Gap
Pumping Plant, some 28O miles to the
south. Included in that reach are
five of the nine major pumping
plants on the aqueduct.
The Tehachapi Crossing facilities
(Tunnels Nos. 1, 2, and 3, and the
4 .7-mile-long Carley V. Porter Tun-
nel) were completed during 1970.
The lengths of these tunnels total
nearly 8 miles. Water will begin
flowing through the Tehachapis in
June 1971. The West Branch facili-
ties needed for Initial water
delivery will be completed in the
fall of 1971, and water deliveries
are expected to be initiated from
Castaic Dam in October of that year.
A contract for construction of
Perris Dam at the terminus of the
aqueduct was awarded in October
1970. The project is on schedule,
and the prospects of meeting the
target date for delivery of project
water to the West Branch contractors
in 1971 and the East Branch contrac-
tors in 1972 and 1973 seem excellent
indeed.
-19-
CHAPTER III. PLANNING FOR
WATER RESOURCE MANAGEMENT
The State of California has long
recognized that the growth and well-
being of its economy require ade-
quate water supplies. The State
has traditionally assumed responsi-
bility for providing guidance and
leadership in planning for the
orderly use and development of its
water resources, as enunciated in
Section 105 of the California Water
Code, which states:
"It is hereby declared
that the protection of the
public interest in the devel-
opment of the water resources
of the State is of vital con-
cern to the people of the State
and that the State shall deter-
mine in what way the water of
the State, both surface and
underground, should be devel-
oped for the greatest public
benefit."
This policy has been elaborated and
detailed in many subsequent pro-
visions of the Water Code and forms
the basic and primary objective of
the planning program of the Depart-
ment of Water Resources.
Planning Considerations
Planning for resources in general is
influenced by public goals and
values as reflected in laws, rules,
regulations and accepted practices.
In the case of water resource plan-
ning, the Flood Control Act of 1936,
which declared that benefits of
federal projects should at least
equal costs, provided a legal basis
for an era of planning which empha-
sized "benefit-cost" in the analysis
of river basin projects. This con-
cept was progressively developed
over the years and today, as defined
in Senate Document 97 (adopted by
the Eighty-seventh Congress in
1962) represents what might be con-
sidered the "traditional approach
to water development planning. This
traditional approach encompasses
both the established concepts and
techniques of economic and financial
analysis, some consideration of
recreational and social benefits,
and specific Informational and
technical criteria which underlie
the project formulation process.
Recent events reveal that social
objectives considered desirable by
society have been significantly
expanded and that certain of these
may not be consistent with the most
economically efficient use of re-
sources. The public interest in
recreation, quality of environment,
healthful ecology, and esthetics
Implies a willingness to forego
opportunity or to spend money in a
way that does not necessarily yield
the highest economic efficiency as
it is now computed. The extent of
public commitment to some of the
emerging environmental demands has
not been defined. Trade-offs of
benefits and/or new financial obli-
gations will be involved.
Most resources planning and develop-
ment have been Initiated from
essentially a single-purpose view-
point for a primary resource, even
though particular developments may
have multiple uses and benefits,
affecting other resources. Water
resource projects have brought into
sharp focus the interrelationships
of resources and resource management
problems with the environment and
economic development. They have
emphasized the need to begin to con-
sider how to carry out coordinated
comprehensive resource management
planning in the total context of the
environment. This indicates the
need for a statewide land use policy
as a prerequisite to the management
of California's resources.
Planners are confronted with the
need to develop new philosophies.
-21-
new concepts, new methodology and
new techniques. The rapid develop-
ment of technology has opened possi-
bilities for new alternative
approaches to water development; and
the increasing concern of the people
regarding environment demands the
development of new and more refined
methods of evaluating the environ-
mental benefits and detriments of
water development.
The Department of Water Resources is
broadening its planning and evalu-
ation processes and techniques to
cover a wider range of water devel-
opment alternatives and th_e increased
application of techniques and con-
cepts of systems analysis. Systems
analysis in the broader sense is the
process of explicitly identifying the
fundamental problems requiring solu-
tion and analyzing a wide scope of
alternatives from the standpoint of
both monetary and nonmonetary values
for the purpose of aiding the
decision-makers in making decisions.
A systems approach might be de-
scribed as a sensitive, analytical
process which helps in formulating
and acting upon required decisions.
The systems analysis methodology has
been widely applied in both business
and government. However, full use
of its techniques in water resource
planning must be further explored
and developed. Successful applica-
tion of this technique holds promise
of broadening the range of alterna-
tives for meeting water development
and other resource needs of the
State, and in incorporating a wider
range of considerations into the
evaluation process.
Decisions regarding management and
utilization of water resources
should be based on a thorough com-
parison of the need for action with
the virtues of retaining options for
the future. Benefits foregone are
real and every effort should be made
to evaluate such benefits before
final decisions are made. All effort
should be made to ensure that deci-
sions made now will minimize delete-
rious effects that might have been
avoided had decisions been made in
such a way as to retain flexibility
for future action.
Water quality assumes increasing
importance as greater pressures
develop on the resources and as the
environmental objectives considered
desirable by society are broadened.
The Department of Water Resources is
charged with broad and continuing
responsibilities toward water quality
management as a part of its role in
water resource management. In order
to exercise this role, new methods
and techniques must be developed for
evaluating the relationship of water
quality to the environment and de-
fining benefits and equating
consequences of water resource
management.
Increased communication with a more
environmentally conscious public is
also important to focus their atten-
tion on water quality management
alternatives and the consequences of
management strategy. There must be
an expanded range of alternatives
available to meet this demand.
Planning Process
The planning process covers the full
range of activities in which objec-
tives are identified and evaluated,
information is analyzed and inte-
grated, plans are formulated and
updated, alternative approaches are
developed, and decisions are made.
The identified objectives are, of
course, a function of the complex
and interrelated social, environ-
mental, ecological, and physical
factors, constituting both forces
and constraints, which must be con-
sidered in developing alternative
management approaches. In reference
to water resources, the planning
process includes not only the phys-
ical needs for urban and agricultural
uses, but the emerging environmental
needs as well. Problems of environ-
mental quality, however, have made
necessary the development of better
methods of identifying and evaluating
water-related environmental ob-
jectives, which requires a wider
range of coordination and an
-22-
expansion of evaluation procedures. Policies, Goals and Plans
Finally, the planning process
provides a procedure for the ratio-
nal selection of specific plans and
programs which leads to the end
product of planning--the implemen-
tation of specific courses of action
to meet the needs of the people.
Public review and comment is an im-
portant aspect of the planning
process .
Development of an overall planning
concept is important to the refine-
ment of the planning process. In
this regard, Figure 1 illustrates
the relationship of the California
Water Plan within the governmental
organization, including policies
and plans; and Figure 2 at the end
of this chapter illustrates the
planning concepts and process for
water resource management in
California. Together, these figures
indicate the relationship of water
resource management to overall
statewide planning, and present the
basic concept of integrated water
resource management planning. These
charts represent both established
relationships and processes and
areas where developmental efforts
are being made.
Figure 2 represents the idealized
planning process which generally
guides the Department. The begin-
ning point and foundation of the
planning process is the California
Water Plan, as updated and supple-
mented by Bulletin No. I6O-66 and
Bulletin No. 16O-70. The studies
and analyses which provide the
basis for supplementing the
California Water Plan are largely
represented by the process de-
scribed in this schematic chart.
However, several significant areas
of the planning concepts and tech-
niques shown in the schematic are
being improved and refined.
The overall water resource management
planning process as illustrated in
Figure 2 consists of three major
sections. These are described in
the following sections.
Although planning is a continuous
process with feedback and readjust-
ment of earlier phases, this portion
of the diagram in Figure 2 is the
beginning point. It is represented
by the California Water Plan as
supplemented and updated by the
Bulletin I60 series; and the various
policies, goals and statewide plans
which have impacts upon water
resource management.
The policies and plans of the State
of California as a whole and the
specific state development policies,
shown in Figure 1, provide the basic
framework, within which the state
water resource management planning
process may be conducted in proper
perspective. The state development
policies embrace five major areas:
population and human resources;
economic development; land use and
resources; environment; transpor-
tation. These policies provide the
foundation for the development of
the various state agency management
plans. Other departments in the
Resources Agency are in the process
of developing their specific de-
partment plans. The California
Water Plan, as updated by Bulletin
No. 160 of the Department of Water
Resources and supplemented by the
water quality control policies and
water quality control plans of the
State Water Resources Control
Board, represents the master plan
for water resource management in
California.
Although the state planning process
and the State Development Plan
Program have not been completed,
developments in this direction will
substantially improve the total
planning process of the State, and
will have important influences upon
water resource management. It is
through the further integration of
these policies and plans that the
State of California will be able to
consider the problems of resources
management and environment as a
totality, and to develop plans and
programs which are more capable of
-23-
FIGURE 1
RELATIONSHIP OF CALIFORNIA WATER PLAN TO OTHER
STATE ENVIRONMENTAL AND DEVELOPMENT POLICIES AND PLANS
CONSERVATION
NAVIGATION
AND
OCEAN
DEVELOPMENT
FISH
AND
GAME
WATER RESOURCES
CALIFORNIA WATER PLAN (2)
(As supplemented and updated
by Bulletin 160 Series)
(1) The California State Development Plan Program Report discusses these environmental and development
policies in terms of a comprehensive state planning process.
(2) California Water Plan takes into account the impact of the plans of other resources agencies and other
State Departments. Sec. 13141 of the Water Code states that state policy for water quality control and
regional water quolity control plons shall become a part of the California Water Plan. Sees. 13145 and
13225 require consideration of effect of water quality actions on the California Water Plan.
Ik-
meeting the interrelated and complex
problems of an expanding technolog-
ical society. The refinement of
the water resource planning process
and the integration of this process
into the total state planning
process is a major step in this
direction.
Water Resource Management
Analysis Process
This process constitutes the
formulation of alternative water
resource management plans and pro-
grams and is diagramed in the central
part of Figure 2. The central anal-
ysis is carried as a central coordi-
nated statewide planning activity.
At this point in the process all
pertinent information relating to
water management in California is
collected, integrated and analyzed.
This analytical process results in
changes in the California Water
Plan based upon existing conditions,
and provides the necessary infor-
mation for the specific alternative
plans and programs to meet the pre-
sent and emerging water management
needs of the State. It takes into
account water resource management
activities at all levels — federal,
state, local and private. Through
the analytical process, existing
conditions, the emerging problems,
environmental and technological
factors and constraints, and public
policies are brought together and
analyzed from the standpoint of
their impacts upon water resource
management needs and possible
solutions.
The process is carried out simulta-
neously at two levels of planning
studies. First, on a statewide
basis, overall systems analysis is
provided, incorporating those fac-
tors affecting water availability,
use, and disposal, and the economic
and environmental-ecological conse-
quences of changes in availability,
quality, use, and disposal of water.
The second level is concentrated on
a more detailed analysis, focused
on the local regions, service areas,
and individual streams. This
detailed information is required
as input and parameters necessary
for statewide systems analysis of
water management.
The specific factors which go into
the water resource management anal-
ysis are shown in Figure 2 by the
type of studies which are carried
out. The analysis takes into
account all relevant water resource
management alternatives and the
estimated consequences of their
implementation .
Formulation of water resource man-
agement plans and prograjns through
continuous coordinated statewide
planning analysis (broad white
central arrow) is the process in
which all of the information is
integrated and synthesized in a
systems analysis approach. Through
various analytical techniques, in-
cluding simulation, input-output,
and other models, it brings together
projections of future economic de-
velopment, analysis of present land
use patterns and projections of
future trends , water supply-demand
relationships, projection of demand
for water-associated services, in-
tegration of water supply disposal
considerations, and other relevant
factors for identification of those
specific alternative plans and pro-
grams to be considered in meeting
the water management needs of the
State. At many points in the
process, information and opinion
from the public will be sought.
The major areas of expansion and
refinement of the evaluation process
are in the analysis of environmental,
ecological, social, economic, water
quality, beneficial use, and insti-
tutional factors that are pertinent
to water management plans. Advanced
techniques, utilizing computer
technology and associated modeling
techniques, will facilitate consid-
eration of these interrelated
factors. Further, expanded use of
the systems analysis approach will
provide additional input for the
analysis of alternative plans and
programs and the selection of
specific plans and programs for
implementation .
-25-
other Resources Agency studies of
water resources (upper left arrow)
cover the monitoring, coordination
where appropriate, and interpreta-
tion of the studies and plans of
federal, state, and local agencies
that have an impact on the
Department's water resource manage-
ment planning responsibilities.
Definition of future services
(lower left box) is the activity
defining the requirements and objec-
tives for water management plans.
Included in this activity are
studies of the magnitude and timing
of future water demand and water
management needs. Consideration of
water-associated recreation plans,
water quality control plans , flood
control, and floodplain management
are all important aspects of this
phase of planning process.
Capability of major water development
options (lower right box) includes
studies to determine the yield,
physical configuration, and poten-
tial accomplishments of those options
that can physically provide signifi-
cant additional water supplies.
Options available include surface
water impoundment and related convey-
ance systems, ground water basin
operational schemes, interstate
water development (Department par-
ticipation in the U. S. Department
of the Interior's Western United
States Water Plan Study) which
might lead to an out-of-state supply
of supplemental water to California,
desalting, and any other techno-
logical development that might make
available a large supply of fresh
water.
Effect of major changes in social,
economic, environmental, techno-~
logical, and governmental factors
on water demand (upper center box)
is basically the study of "non-
structural" alternatives to water
development. Studies cover investi-
gation of the extent to which major
changes in present institutional
arrangements would reduce or post-
pone the need for additional water
development in California, the
economic and environmental
consequences of such changes, and
the political and legal practicality
of attempting to implement them.
Studies would include consideration
of: (1) reallocation of existing
water supplies and water rights;
(2) planned location of industries,
educational facilities and other
public services; (3) technological
research and development; (4) re-
duction in water use, demand, and
waste water disposal through
pricing policies; and (5) land use
policies.
Effects of water reuse and conser-
vation on water supply, demand, and
environmental quality (upper right
box) is an evaluation of the roles
of water reclamation, watershed
management, evaporation and seepage
suppression, and phreatophyte erad-
ication or control in water resource
management plans. Most of these
options would have economic benefits
of extending the use of an existing
developed water supply. However,
they also have the potential of
greatly affecting the environment.
Water reclamation may offer the
opportunity to reduce overall water
supply and waste treatment costs or
to realize significant environmental
benefits by irrigating recreational
areas and agricultural greenbelts
adjacent to metropolitan areas.
Other options, such as phreatophyte
eradication or watershed management,
can have detrimental ecological con-
sequences by eliminating or reducing
wildlife habitat. Comprehensive
evaluation of each of these options
is important to ensure that all
benefits and detriments are iden-
tified and evaluated, including all
environmental and ecological
consequences.
Decision and Implementation
Activity
This is an objective of the planning
process, resulting in specific plans
and programs to meet the water
resource management needs of the
State. It is in this phase that the
planning process enters into the
-26-
area of decision-making . Also it
is at this point that the tradi-
tional planning process encounters
a major criticism--the criticism
that a broader range of technically
feasible alternatives for meeting
water development objectives should
be made available to the public for
consideration, along with both
tangible and intangible costs and
benefits for each alternative.
Through the use of advanced analyt-
ical techniques it is possible to
analyze alternative approaches,
particularly those based upon devel-
oping technology, and to provide a
more intensive analysis of the
environmental, social and economic
impact of these alternatives for
public review. Thus, an essential
product of the analytical process
is to provide a broad range of
alternatives which may be considered
by the public and the Legislature.
These alternatives or options would
be presented in terms of economic,
social, and physical consequences.
An important consideration at this
point of the process is that the
final decisions should provide a
wide degree of flexibility for the
future, and foreclose as few choices
as practicable.
The identification of alternative
plans and programs lays the founda-
tion for the necessary public and
legislative reviews which lead to
the selection of specific water
resources proposals and plans.
Selected plans and programs would
be implemented to meet the water
resource management needs of the
State after review and comment by
the public.
At each step of the process--whether
it be in the analytical process
where information is fed into the
system, the identification of alter-
native plans or programs, the
selection of specific water resources
plans and programs, or the actual
implementation of such plans and
programs--and at whatever govern-
mental level this may take place,
the resulting information, decisions
and actions influence the developing
California Water Plan. Periodically
in the Bulletin l60 series, the
Department of Water Resources ana-
lyzes and evaluates all of the
changes, present and projected, and
supplements the California Water
Plan as best it can be foreseen at
the time of publication.
In Summary, as we enter the decade
of the '70s the planning program
of the Department must be and will
be further broadened to reflect
adequately the increasing concern
for environmental and ecological
considerations. Many of the tra-
ditional concepts and techniques
that were both relevant and suffi-
cient for water development planning
in the past must be scrutinized and
reevaluated to reflect both changing
technology and changing values.
The Department must provide for the
water needs of the State in such a
way as to minimize the adverse
effects of project construction on
the natural environment and, at the
same time, to enhance the environ-
ment. This approach necessitates
the broadening of choice among
alternatives to consider parameters
other than maximization of net
economic benefits and least cost
only. It also requires flexibility
in the planning process so as not
to foreclose the available options
by premature selection of a course
of action. The concepts of re-
duction of damage to the environ-
ment and enhancement of the
environment will loom large in the
decision-making process in the
future.
-27-
FIGURE 2
POLICIES, GOALS
AND PLANS
WATER RESOURCES MANAGEMENT ANALYSIS PROCESS '
PREPARATION
OF
BULLETIN
REVISION OF CALIFORNIA WATER PLAN BASED ON PLANNING PROCESS. ^
EFFECT OF MAJOR CHANGES IN
SOCIAL, ECONOMie, ENVIRON-
MENTAL, TECHNOLOGICAL AND
GOVERNMENTAL FACTORS ON
WATER DEMAND
EFFECTS OF WATER
REUSE AND CONSERVATION
UN WATER SUPPLY, DEMAND.
AND ENVIRONMENTAL
QUALITY
FORMULATION OF WATER RESOURCES MANAGEMENT PLANS AND PROGRAMS
THROUGH CONTINUOUS STATEWIDE PLANNING ANALYSIS
PROJECTION OF FUTURE ECONOMIC
DEVELOPMENT.
ANALYSISOF PRESENT LANDUSE
PATTERNS AND PROJECTION OF
FUTURE TRENDS.
WATER SUPPLY ■ DEMAND RELATION-
SHIPS
PROJECTION OF DEMANDS FOR WATER
ASSOCIATED SERVICES
INTER-RELATIONSHIP OF WATER USE
AND WATER QUALITY.
INTEGRATION OF WATER SUPFL
.DISPOSAL CONSIDERATIONS IN
MANAGEMENT PLANS-
SIMULATION. INPUT-OUTPUT, AND|
OTHER MODEL STUDIES.
ENVIRONMENTAL AND ECONOMIC ,
IMPACT STUDIES OF WATER USE j '
AND DEVELOPMENT OPTIONS.
DEFINITION OF FUTURE SERVICES
A. MAGNITUDE AND TIMING OF FUTURE WATER DEMAND AND
WATER MANAGEMENT NEEDS.
B. LAND USE PATTERNS AND TRENDS.
C. WATER QUALITY CONTROL PLANS.
D. FISH AND WILDLIFE PLANS.
E. FLOOD CONTROL CONSIDERATIONS.
F. RECREATION PLANS.
CAPABILITY OF MAJOR WATER DEVELOPMENT OPTIONS
A. SURFACE WATER
B. GROUND WATER
C- INTERSTATE WATER DEVELOPMENT
D. DESALTING
E. OTHERS
INPUT FROM PUBLIC
ENTERS THIS PROCESS
AT A NUMBER OF POINTS.
PLANNING FOR WATER RESOURCES
MANAGEMENT IN CALIFORNIA
DECISION AND IMPLEMENTATION
OF WATER MANAGEMENT PROGRAMS AND PLANS
DECISIONS AND NEW PROGRAMS AND PLANS
alternative
specific plans an
'rograhs for hj-e
managemen-
SELECTION OF
SPECIFIC WATER
RESOURCES
PROGRAMS AND
PLANS
my
CONTINUOUS PROCESS
INFORMATIONAL INPUT
BASED ON STUDIES BY
DEPARTMENTS ANDOTHERS)
.29-
CHAPTER IV. WATER DEMANDS
Following publication of Bulletin
No. 16O-66 the Department undertook
a four-year study and analysis of
demands for water service through-
out the State. These demands were
projected to years 1990 and 2020 to
provide an analytical framework for
long-range planning necessary for
the most effective development and
use of additional water supplies
from the various potential sources.
This chapter summarizes the demands
for water on a statewide basis.
Some of the principal determinants
of future demands such as popula-
tion and irrigated agriculture are
discussed, as are the important
aspects of recreation, fish and
wildlife, flood control, and water
quality.
Future Economic
Development
Urban and agricultural uses of
water account for nearly all of the
water presently consumed in
California. Estimates of popula-
tion and related industrial and
commercial development provide the
basis for determining urban water
demands. Agricultural water needs
are dependent upon food and fiber
requirements and irrigated acreages
considered necessary to meet those
requirements. This section dis-
cusses these aspects of water use.
Population
Projection of population is basic
to water planning studies. In
many respects it is the key to
other water development needs such
as agricultural production, flood
control, electric power, recreation,
fisheries, wildlife and water
quality. Population growth has
become the focal point for many
environmental and ecological con-
siderations which are becoming of
increasing concern. For these
reasons it is important to under-
stand the direction and general
level of present and anticipated
future population trends.
Between 1940 and 197O the State's
population more than tripled, grow-
ing from about 6 million people to
slightly under 20 million. Gener-
ally California's population has
doubled every 20 years since i860.
A continuation of such rates would
suggest a state population of
40 million in I99O and about 60
million by the turn of the century.
Two factors have occurred in the
past decade which indicate that such
levels of population growth in
California are unlikely. The first
relates to a national phenomenon--
people's attitudes toward population
and family size in particular. The
second relates to a particularly
important component of California's
growth- -namely, massive in-migration.
As to the first, the rapid decline
in fertility rates during the past
decade is one of the most striking
of recent demographic trends. As
recently as I967 the U. S. Bureau
of the Census published a series of
population projections for the
Country as a whole, corresponding
to four birthrate series. These
are depicted in Figure 3 as A through
D. Each has been experienced at
some time in the past. In August
1970 the Bureau revised its esti-
mates, dropping series A as unreal-
istic and adding series E which
would result in a more or less
stable population The magnitude of
the difference in total population
may be seen in the tabulation at the
top of the following page.
A constant net migration of 200,000
was used to depict the impact of the
change in birthrates on the popula-
tion projections for the State. The
200,000 figure is quite significant
in that it reflects a reduction
-31-
U. S.
Population
: Correspond!
ng California
Series
(millions )
: Population
(millions )
: 1980
: 1990
: 2000 : 2020
: 1980
: 1990 :
2000 :
2020
A
240
286
337 488
25.6
32.8
41.0
65.8
B
237
277
321 440
25.2
31.8
38.9
59.1
C
232
266
301 386
24.7
30.4
36.4
51.5
D
228
255
281 336
24.2
29.0
33.9
44.7
E
226
248
266 299
23.9
28.3
32.1
39.6
from 300,000 vjhich for so many years
was typical in California. However,
in the period since 1964 there has
been a progressive and substantial
drop in annual net migration to
California, leading to the choice of
the lower level as the basis for
the Department's presently adopted
projections, as Indicated in the
following paragraph.
In view of the changes occurring in
fertility rates and migration levels,
the California Department of Finance
made extensive revisions of popu-
lation estimates for California in
January 1970. Projections were
made for five-year intervals to
year 2000. Series D birthrates and
an average annual net migration of
200,000 were assumed throughout the
period. These estimates were
adopted by the Department as repre-
senting the "official" projections
of the State and are so reported in
this bulletin. They are the basis
upon which the water demands for the
State have been determined.
F.gur,
UNITED STATES FERTILITY SERIES
THOUSANDS OF CHILDREN PER 1000 CHILDBEARING WOMEN
3,350
3,100
2,775
2,450
FERTILITY SERIES
'series D used for making CALIFORNIA POPULATION PROJECTIONS
-32-
T
T
5^%j*-^^^ ^^ "^- ^:
Wildlife an important water demand consideration
:;f'-'i>;
U.S. Bureau of Reclamati
Since the Department of Water
Resources' planning period extends
to 2020, it was necessary to
extrapolate the Department of
Finance population estimates to that
date. It was also necessary for the
Department to distribute the state
totals among the 11 hydrologic areas
adopted for the studies reported on
in this bulletin and depicted in
Figure 4. Allocations to the study
areas were based on an analysis of
trends, including natural increase
and net migration for individual
counties within the appropriate
hydrologic areas . The projections
of population for California and
the 11 hydrologic study areas are
summarized in Table 1 and Figure 5.
In general, the projections reflect
a continuation of historic growth
patterns. Those areas with large
present populations that have under-
gone the largest growth in the past
are expected to record the largest
gains in the future. The coastal
area of California, extending from
San Francisco Bay southward to the
Mexican border, is the prime growth
area, accounting for all but
5 million of the expected 25 million
increase in population between 1970
and 2020.
TABLE
1
TOTAL
BY
POPULATION
HYDROLOGIC
1967, 1990,
IN CALIFORNIA
STUDY AREA
2020
(in 1,000
s)
Hydrologic Study Area
1967
1990
2020
North Coastal
180
210
300
San Francisco Bay
4,320
6,500
10,100
Central Coastal
750
1,200
2,200
South Coastal
10,510
16,000
23,900
Sacramento Basin
1,140
1,600
2,300
Delta-Central Sierra
400
650
1,100
San Joaquin Basin
410
610
1,0 00
Tulare Basin
910
1,200
1,800
North Lahontan
40
70
100
South Lahontan
220
590
1,300
Colorado Desert
220
370
600
TOTAL
19,100
29,000
44,700
-34-
F igure 4
STATE OF CALIFORNIA
THE RESOURCES AGENCY
DEPARTMENT OF WATER RESOURCES
HYDROLOGIC STUDY AREAS
OF CALIFORNIA
NC - NORTH COASTAL
SF -
CC -
SC -
SB -
SAN FRANCISCO BAY
CENTRAL COASTAL
SOUTH COASTAL
SACRAMENTO BASIN
DC - DELTA- CENTRAL SIERRA
SAN JOAQUIN BASIN
TULARE BASIN
NL - NORTH LAHONTAN
SOUTH LAHONTAN
CD - COLORADO DESERT
_,7
"^
■35-
Figures
CALIFORNIA'S HISTORICAL and PROJECTED
POPULATION GROWTH
Stretch-out of some 10 years before
an additional source of water is
needed to augment the initial facili-
ties of the State Water Project.
This will be discussed in
Chapter VII. The impact involves
not only the reduction of urban
water demands, but also a lower
agricultural water demand. On the
other hand, if there is a resurgence
in California's growth, as there has
so often been in the past, an addi-
tional water supply could be needed
at an earlier date.
Other aspects of future population
growth should be recognized. There
are many pressures, problems, and
concerns growing out of the con-
gestion and pollution associated
with large urban areas . It is
possible that changing federal,
state, and local planning policies
would significantly affect future
urban development. One approach
might be a redistribution of people.
This possibility is explored in
some detail in Chapter VIII with
emphasis on its impact on water
development needs, use, waste dis-
posal, and other possible impacts
such as air pollution. It also
serves to illustrate the possible
Impact on water demands in highly
urbanized areas as a result of a
drastic change in population growth.
The projections shown in Table 1
represent the Department's best
Judgment at this time. Although
the listed projections reflect
recent downward trends in birthrates
and net migration to California,
they should not be considered either
the possible high or possible low,
but a median projection. As shown
in Figure 6, the general range of
possibilities has shifted downward.
The median projection now approxi-
mates very closely the low projec-
tion made by the Department some
12 years ago.
The impact of future population
levels on the timing of need for
future water supplies can be quite
significant. The difference
between earlier estimates published
in Bulletin No. 160-65 and those
in this bulletin suggest a
Industrial Development
Employment is expected to grow at
about the same rate as population,
resulting in approximately 4 million
new Jobs by 1990. At the same time
shifts in employment are expected to
continue between major industrial
categories. On-farm employment,
reflecting further technological
advances, wLll show declines while
other natural resource-based
Industries such as mining, forestry,
and fisheries, may reflect modest
gains. Manufacturing employment
will have increased by about 700,000
over the next 25 years, but the
largest increases are expected to
occur in the service and govern-
mental categories in response to
the demands of an expanding and
affluent society.
-36-
HIGH , MEDIAN and LOW POPULATION PROJECTION
STATE OF CALIFORNIA
PRIOR STUDIES CURRENT STUDIES
1990
PRIOR STUDIES CURRENT STUDIES
2020
Industries requiring large quantities
of water will reflect the general
growth trends. For the most part
the most significant water-using
industries are directly related to
Califor-iiia's population and its
growth in the demands for goods and
services. Ten industries are either
related to agricultural or timber
production.
In preparing estimates of urban
water demands, the general practice
is to include industrial water needs
with the other components of urban
use, making Judgments concerning
overall per capita water use in
each area. However, in certain
areas, analysis indicated that
specific high-water-using industries,
independent of the size of the
local population, would account for
large proportions of the total
urban water use. In these cases
growth and needs of such industries
were evaluated separately. The
resulting industrial water demands
were added to the water needs
related directly to population to
determine total urban water demands.
-37-
Electric Power Development
Increases in population per capita
consumption, and industrial-
commercial uses of electricity have
resulted in a phenomenal rate of
growth in electric power demands,
especially in recent years. These
same factors will contribute to the
very substantial growth in genera-
ting requirements shown in the
tabulation at the bottom of this
page.
Until the 1950s, the chief source
of electrical power in California
was hydroelectric generation.
However, as hydroelectric sites
have become more scarce and costly,
other sources of power have become
increasingly important in meeting
the growing power demands. While
it is anticipated that some addi-
tional capacity will be realized
through enlargement of existing
facilities, the major sources of
additional hydroelectric power
during the next 50 years will prob-
ably come from the installation of
pumped storage plants.
A pumped-storage plant uses lower-
cost energy available from other
generating sources during periods
of low power demand to pump water
from a lower to an upper reservoir.
When additional generating capacity
is required, the water is allowed
to flow from the upper to the lower
reservoir through a pumplng-
generating unit and thus generate
higher-value electric power.
The quick response and generally
superior operating flexibility and
reliability of hydroelectric equip-
ment make the pumped-storage unit
ideal for peaking operation and for
system reserve service.
Steam electric plants will be relied
upon to supply a greater portion of
total power requirements in the
future. Of the estimated 412,000
megawatts of the power resources
required in 2020, more than 300,000
megawatts or over 80 percent may have
to be provided by additional thermal
plants. In 1970 fossil fuel plants
were the primary source of energy
with a generating capability of
about 20,000 megawatts. Nuclear-
fueled plants had a capacity of
about 493 megawatts. In all prob-
ability nuclear-fueled plants will
be emphasized in the coming decades
for environmental and economic
reasons .
The projected emphasis on nuclear-
fueled plants will enhance the
desirability of pumped storage.
Nuclear plants are relatively high
capital cost and low energy cost.
To obtain their full economic poten-
tial, nuclear plants must be kept
operating at or near maximum plant
capability to the extent possible.
Pumped-storage plants require low-
cost pumping energy for economical
operation. Thus, when a power sys-
tem includes both nuclear and
pumped-storage units the nuclear
units can be kept operating at or
near full capability during periods
of low power demand, and furnish
energy for operation of the pumped-
storage plants. Also, the nuclear
units provide the low-cost energy
necessary to make the pumped-
storage operation economical.
The projections of electricity
generated by primary sources of
power is illustp?ated in Figure 7.
Generating requirements
(megawatts )
Peak Demand (megawatts)
Population (millions)
Per Capita Energy Require-
ment ( megawatt -hours )
1970
32,100
25,000
20
1990
110,000
92,000
29
18
2020
412,000
340,000
45
46
-3,8-
F igure 7
GENERATION OF ELECTRIC ENERGY BY PRIME SOURCE
TO MEET FUTURE POWER DEMANDS
500
400
300
200
Careful consideration will be neces-
sary in siting future plants. Until
recently, utilities have been able
to find suitable locations for steam
plants. However, serious problems
exist at this time for a number of
reasons: land area requirements;
waste heat discharges; air pollution
from fossil-fuel-fired plants;
seismic design requirements; and
required distances from population
centers for nuclear plants. Because
of the many and varied siting
YEAR
problems involved, a State of
California Powerplant Siting Commit-
tee has been established. The Com-
mittee is charged with evaluating
all proposed steam electric power-
plant sites.
The availability of land will be an
important consideration. The tabu-
lation below indicates the land
requirements for three types of
thermal powerplants of 6,000 megawatts
using various cooling arrangements.
Cooling System
Plant Type (acreage requirements)
Nuclear
Gas and Oil
Coal
Once-through
Cooling Towers
Cooling Pond
400-800
500-1,000
6,000-12,000
200
400
4,000-6,000
800-1,000
1,000-1,200
5,000-9,000
-39-
Spence Air Pho
1954
r ft
Spence Air Pho
1960
"/n Los Angeles, Orange, Riverside
taken place on agricultural lands. "
Counties over 90 percent of urban expansion . . . has
Agricultural Development
California has been the Nation's
leading agricultural state for more
than 20 years. In 1970 the value of
production approximated $^ billion.
V/hile California is expected to
retain Its prominence in agriculture
during the ' 70s and beyond, the
Industry will undoubtedly experience
substantial problems, including: a
dampening of prices caused by over-
production of som.e commodities;
rising production costs; a highly
competitive market for credit; and
continued pressure on land resources
with attendant rises in land values
and taxes. In fact, urban pressures
are one of the foremost problems
facing the industry.
During the past two decades 30,000
to 40,000 acres a year have been
required to accommodate California's
growth in population and commercial
developments. Generally, about half
of this growth has occurred on
highly productive agricultural
lands. In Los Angeles, Orange,
Riverside, and Santa Clara Counties
over 90 percent of the urban expan-
sion, or 14,000 acres annually, has
taken place on agricultural lands.
In some counties during the past
few years all additional urban
development took place on crop-land.
Anticipated reductions in the future
rate of population growth, coupled
with higher densities, will reduce
the absorption rate somewhat. But
the value of land will remain high
and there will be increasing pres-
sures from an assortment of uses
including recreation, wildlife
habitat and preserves. Figure 8
illustrates the decrease in remain-
ing irrigable lands (lands suitable
for crop production) over the next
50 years .
It will be noted in Figure 8 that
in 2020 California will still have
a significant supply of lands avail-
able for agricultural development.
However, in the major agricultural
regions of the State much of the
best agricultural land will have
been put to some use by 2020 if pres-
ent trends continue. In the San
Joaquin and Tulare Basins an esti-
mated 72 percent of total irrigable
lands will be developed by that
date. In prime agricultural areas
such as Yolo and Sutter Counties
and in Salinas Valley there probably
will be practically no remaining
undeveloped agricultural areas. In
the highly urbanized regions of the
San Francisco Bay and South Coast,
agriculture will be virtually elimi-
nated by urban encroachment.
Because of the many and varied pres-
sures on agriculture, it is antici-
pated that California farming will
continue to evolve Into larger more
efficient operations. Crop patterns
will become even more Intensive with
an emphasis on high-value crops.
Generally, the trend is expected to
be toward the vegetables, fruit,
and nuts categories in which Califor-
nia has a proven competitive
advantage .
The present (I967) and projected
irrigated acreage in California is
shown by hydrologic study areas in
Table 2. The location of presently
irrigated and potentially irrigable
lands is shown on Plate 2 entitled
"Irrigated, Irrigable, and Urban
Lands^.
The specter of overproduction men-
tioned at the beginning of this
section will be a matter of periodic
market adjustments as it has been in
the past. The next few years are
expected to be particularly difficult
for the producers of commodities
such as fruit, nuts, cotton, and
perhaps others. Adjustments are
expected to take place either in the
form of price reductions, reduced
acreages, changing crop patterns, or
an increase in California's share of
market.
The longer-ran^^e projections of Irri-
gated acreage appearing in this
bulletin presume that the adjustments
will have been made and that there
will be a need for the additional
irrigated acreages shown in Table 2.
This has been accomplished by relat-
ing the supply of food and fiber to
demand. The latter has been deter-
mined from Increases in the projected
JJI-
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Si
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8S
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3
3
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a
o
z
<
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o
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8SS
gg
S8S
RS3
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3 8 S
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8 S
8 8
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R3
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ss
8 g
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SS
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-42-
Figure 8
PRESENT AND PROJECTED LAND USE
16
14
-
12
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10
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u
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en
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3
1967
1990
2020
population, changes in per capita
consumption, and export requirements.
Taken together, these factors result
in a total production requirement
for food and fiber. Based upon work
of the University of California
Agricultural Extension Service an
allowance was made for increasing
future crop yields. Acreages
necessary to meet anticipated food
consumption were derived by dividing
production requirements by the
yields per acre.
In summary, the projected Increase
in irrigated acreage over the next
50 years will show a marked de-
crease from projections based on
earlier trends. Historical
increases from 19^0 to the present
and projected increases to 2020 are
shown in Figure 9.
The lower projections result from
continued improvements in crop
yields, enabling increased produc-
tion on less acreage, and lower
trends in the State's and the
Nation's population.
Water Demand
Future urban and agricultural water
demands for 199O and 2020 were
derived as the product of economic
growth, as discussed in the previous
section, and appropriate water use
factors. Needs for other uses such
as recreation, fish and wildlife are
-43-
CALIFORNIA S HISTORICAL ond PROJECTED
NET IRRIGATED ACREAGE
1930 — 2020
AVERAGE ANNUAL INCREASE IN 1000 S OF ACRES.
also Included. The statewide sum-
mary of water demands presented in
this section is actually a composite
of regional studies conducted by
the Department and presented in
Chapter VI. The possible ways and
means of meeting the projected
water demands are discussed in
Chapters V and VI. The resulting
impact on the need for future facil-
ities in the State Water Project and
Central Valley Project is presented in
Chapter VII.
In total, the Department's findings
indicate that water demands in the
State are expected to increase
between 11 and 12 million acre-feet
from 1967 to 2020. The historical
and projected growth pattern of
applied water demands for urban and
agricultural purposes is shown in
Figure 10.
The remainder of this chapter dis-
cusses the principal uses contrib-
uting to increased water demand,
namely for urban and irrigated
agricultural uses. It also covers
other uses of water including recre-
ation, fish and wildlife, and flood
control. The chapter concludes with
a discussion of water quality
considerations .
It will be noted in the discussion
that water demands have been refer-
red to as either applied or net.
In water resource planning it is
necessary to know and understand
both. Applied water is an expression
of the quantity of water that must
be made available at the actual
place of use. Net water demand is
the quantity of water that must be
delivered to a service area as a
whole, including conveyance losses
within the area that are not recov-
ered for reuse. As a general rule,
net demand is less than applied de-
mand due to the possibilities of
reuse within the service area. An
exception to this definition occurs
Figure 10
CALIFORNIA'S HISTORICAL and PROJECTED
APPLIED WATER DEMANDS
1930 — 2020
.14 n.
in the Colorado Desert where very
little reuse is possible because of
water quality considerations. In
this case net demands at the actual
place of use are essentially the
same as applied demands. However,
conveyance losses, amounting to
about one-half million acre-feet,
do not reach the place of use,
thereby constituting an increment
of net demand. This results in the
net diversion demand being greater
than the applied demand.
Urban Water Demands
California is a highly urbanized
and industrialized state. The need
for water to meet requirements for
household uses, fire protection,
irrigation of lawns and gardens,
parks, golf courses, and indus-
try and commerce has generally
increased with the population and
growth of the economy.
Over the years the Department has
collected urban use values for
cities throughout the State and
from a large number of water
agencies and manufacturing estab-
lishments. Per capita water use,
or average water used per person,
has been determined by relating
total water deliveries for all
urban purposes to the population
served. Historical data identify
trends in water use; when combined
with the many factors influencing
use, such as climate, urban densi-
ties, and industrialization, they
serve as a basis for projecting per
capita use.
Generally, the historical trend in
per capita water use has been up-
ward. The evidence seems to indi-
cate that use increases with a
rising standard of living. The
projections, however, have been
tempered by several considerations.
Anticipated pressures on land and
attendant development costs will
tend to increase densities and de-
crease average lawn and garden
areas, thereby decreasing outside
water use. There is also some
likelihood of reduced water use in
the industrial sector. The growing
concern over pollution and stronger
effluent controls may result in
less water intake. Increasing water
costs and waste water treatment will
encourage technological changes and
economies in water use.
On a more localized basis, water
use varies considerably from city
to city, region to region. The per
capita projections shown in Table 3
are weighted average values derived
from historical data and Judgments
regarding a number of factors influ-
encing water use in each region.
These factors include the nature of
the urban complex, whether heavily
industrialized or primarily resi-
dential; densities as related to
average lot size; climate; and
others, A more complete discussion
on this subject is published in
Department of Water Resources
Bulletin No, 166-1, "Municipal and
Industrial Water Use".
The combination of changes in per
capita use, increases in population,
and expansion of the economy results
in an applied urban water demand of
nearly 12 million acre-feet by 2020.
This compares to 4,4 million acre-
feet in 1967 and 7.4 million acre-
feet in 1990. Applied and corres-
ponding net water demands are
summarized in Table 4, Unless there
are drastic reductions in Califor-
nia's future growth or a dramatic
shift in population distribution as
suggested in Chapter VIII, most of
the increased water demands will
occur in regions that are already
importing water. Even if population
shifts occur, the findings in
Chapter VIII indicate that further
water developments will be necessary.
However, the date at which addi-
tional water must be made available
for urban use has been affec1;ed by
the general reduction in population
increase .
In the South Coastal area, a very
important water import area, the
combination of a slower buildup in
urban growth and less per capita
water use has contributed greatly
to lower net water demands than pre-
sented in Bulletin No. I6O-66. As
stated earlier, these considerations
-45-
TABLE 3
ESTIMATED URBAN WATER USE
(gallons per capita— per day)
Hydrologlc Study Area
North Coastal^
San Francisco Bay
Central Coastal
South Coastal
Sacramento Basin—'
/
3/
1967
1990
2020
160
140
130
170
200
220
200
210
210
180
190
200
350
350
350
320
280
260
370
390
420
370
350
350
^
V
V
280
320
320
380
400
400
Delta-Central Sierra—'
San Joaquin Basin
Tulare Basin
North Lahontan
South Lahontan
Colorado Desert
1/ Average number of gallons of water used per person, per day.
Based on projected urban water demands and urban population served,
2j VJater demands for pulp and paper production not included in per
capita values.
^/ Based on urban use in valley floor portion only. Recreational
and "second home" use in Sierra foothills not Included.
4/ Total urban water demands for this area, as shown in Table 4,
were determined by means other than per capita water use values.
Note: The above figures are weighted averages and
reflect a considerable range of per capita
values for communities within the study areas.
The Department's Bulletin No. I66-I should be
referred to for a more detailed breakdown of
urban water values and discussion regarding
the various factors affecting urban water use.
will delay the timing of need for an
additional water supply in relation
to the timing estimated in Bulletin
No. 160-66.
The significance of the projected
growth in urban demands may be seen
in Figure 11. Comprising only
13 percent of total water demands
in the State in I967, urban needs
will account for 25 percent by 2020.
On an incremented basis, total
applied water demands are expected
to increase about 12 million acre-
feet during the I967-202O period.
Of this amount, 7.5 million
-46-
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^R 8^
3SS SaS
19. 881
^"Si, °*a §1^
cy58 Q^t- -Hcyfo rooS ^3(
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^S 8 38
lA CM a5 oo
888 S3S
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-47-
FIGURE n
1967
URBAN WATER DEMAND 4,370,000 A.F
AGRICULTURAL WATER DEMAND 31,080,000 A.F
MISCELLANEOUS 475,000 AF
TOTAL WATER DEMAND 35,925,000 A.F
1990
URBAN WATER DEMAND 7,370,000 A.F
AGRICULTURAL WATER DEMAND 34,060,000 AE
MISCELLANEOUS 745,000 AF
TOTAL WATER DEMAND 42,175,000 A.F
2020
2 URBAN WATER DEMAND
11,850,000 A.F
I I AGRICULTURAL WATER DEMAND 35,260,000 A.F
HH MISCELLANEOUS 925,000 A.F
TOTAL WATER DEMAND 48,035,000 AF
PROJECTED GROWTH OF APPLIED WATER DEMANDS
STATE OF CALIFORNIA
-U8-
acre-feet, or more than 60 percent,
will be due to population and
related urban growth.
Agricultural Water Demands
Agriculture remains far and away the
largest water user in California and
is expected to remain so throughout
the period of analysis. Total
applied water demands for irrigated
agriculture amounted to 31 million
acre-feet in I967 and is projected
to increase to 3^ million acre-feet
in 1990 and to more than 35 million
acre-feet in 2020. Although this
increase is only about half that
expected for urban purposes, irri-
gated crops will still account for
73 percent of total applied water
demands in 2020 (Figure 11).
Applied water requirements for irri-
gated agriculture are determined by
multiplying the estimates of irri-
gated acreage for specific crops by
appropriate unit water use values.
Like urban per capita water use
values, crop requirements vary from
area to area depending on climate,
farming practices, and soil con-
ditions. Weighted averages reflect
the crop pattern In each region and
are summarized in Table 5.
In general, comparatively little
change in unit water use values is
expected during the study period.
Change that does occur will result,
to a large extent, from changes in
cropping patterns and increases In
irrigation efficiencies, especially
in areas having high water costs.
TABLE 5
IRRIGATED AGRICULTURE
APPLIED UNIT
WATER
JSE VALUES
*
(acre-feet per
acre)
Hydrologic Study Area
1967
2020
North Coastal
2.7
2.7
San Francisco Bay
2.6
2.2
Central Coastal
2.3
2.4
South Coastal
2.0
2.3
Sacramento Basin
4.0
4.0
Delta-Central Sierra
3.0
2.9
San Joaquin Basin
4.4
3.8
Tulare Basin
3.1
3.2
North Lahontan
2.9
3.4
South Lahontan
6.1
5.4
Colorado Desert
4.9
4.8
■^Weighted average for
all present and
probable
future crops.
1
-49-
March 1968
.•*-*.'.
October 1970
Impact of water on agricultural development State Water Project serving western Kern County
Total applied agricultural water
demands summarized in Table 4 exceed
those in Bulletin No. I6O-66 by more
than one and a half million acre-
feet in 1990. This occurs in spite
of a reduction in projected irri-
gated acreage. Field studies con-
ducted over the past four years
Indicate that the consumptive use
of water of some crops is signifi-
cantly greater than earlier esti-
mated values. By 2020 the reducticn
in projected irrigated acreage is
significant enough to more than
offset the increase in unit use
values and applied water demands
are less than previously
estimated.
Bulletin No. I6O-66 did not report
net values for individual purposes.
Therefore, a comparison of net agri-
cultural water demands cannot be
made. With a few exceptions,
however, agricultural water demands
are far and away the most signifi-
cant element of a region's total
demand, and changes in total net
demands largely reflect changes in
that sector. For the most part, the
implication is that net agricultural
water demands are greater than
reported in Bulletin No. I6O-66.
The reason for this increase is
that the Department's studies
since publication of that Bulletin
have provided much new and addi-
tional information regarding return
flows in areas throughout the
State. This information, in combi-
nation with additional knowledge of
consumptive use of water and on-
farm irrigation efficiencies,
served as a basis for making sig-
nificant changes in some areas.
Since the need for additionally
developed water supplies is con-
tingent upon the needs of a service
area (represented by net water
demands), the determination of the
latter carries great importance.
Chapter VI describes the relation-
ship of net water demands and sup-
plies in each hydrologlc region,
and Chapter VII discusses the
impact of the projections In re-
lation to water supplies on the
timing of future facilities to the
State Water Project and the Central
Valley Project.
Water Demands for Electric
Powei* Generation
All large thermal powerplants con-
tain condensers requiring large
quantities of water for cooling
purposes. Once-through cooling,
the most economical cooling process,
requires a large body of water from
which the water is withdrawn and
returned. To reduce costs it is
desirable that such plants be
located close to a water supply.
Today, the cooling water required
for a 1,000 megawatt unit is
roughly 1,500 cubic feet per second.
The amount of water actually con-
sumed In the cooling process is
considerably less. A modern 1,000
megawatt unit operating essentially
continuously will use between
15,000 and 20,000 acre-feet of water
per year.
The unit amount of water required
for cooling will undoubtedly de-
crease with more efficient plants
in the future. While waste water
can provide a limited supply, the
limited supply of fresh water and
the availability of sea water
coupled with the expected growth In
population along California's coast
will influence the siting of a
significant portion of future
thermal plants .
The amount of fresh water to be used
for cooling in thermal powerplants
will be dependent on a large number
of factors, such as siting consid-
eration, cost and availability of
water. However, it is presently
estimated that only about 100,000
acre-feet of fresh water will be
used annually for powerplant cool-
ing by 2020, on the premise that
powerplants will be located near the
ocean.
-51-
Recreation, Fish and
Wildlife and Related
VJater Development
It is the policy of the State of
California to provide its citizens
with the fullest possible oppor-
tunity for recreation. This
involves a variety of facilities
throughout the State. The task
required to meet this obligation
will be formidable. Estimates
place outdoor use at 1.5 billion
recreation-days a year by 1990 and
2.5 billion in 2020. This compares
to 218 million in 196O. The
increase in demand for recreational
facilities comes at a time when the
competition among land and monetary
resources is very keen. Government
at all levels, the private sector
and a general willingness of people
to spend additional dollars for
recreation will be required to meet
the growing demand.
Since about 60 percent of all out-
door recreation involves water-
associated activities, water devel-
opments have a major role to play.
This section discusses some of the
more important policy and financial
considerations affecting this role.
Major Policies of
federal and State
Water Development Agencies
Both the Federal Government and the
State of California have had long-
standing policies with regard to the
incorporation of recreation services
into water development projects. At
the federal level, the most recent
policy statement having far-reaching
implications is P.L, 89-72. Very
briefly, the document states that
outdoor recreation and fish and
wildlife development will receive
full consideration as purposes in
project formulation and evaluation,
and provides for federal financial
participation in the development and
operation of recreation and fisheries
and wildlife enhancement features,
if there is major financial partici-
pation by nonfederal activities.
In California, the Davis -Dolwlg Act
of 1961 serves as the primary source
of state policy concerning recreation
and fish and wildlife at state-
constructed water projects. The Act
declares recreation and fish and
wildlife enhancement to be among the
purposes of state water projects,
and requires that all reasonable
actions be taken to preserve fish
and wildlife. It makes clear the
legislative intent of substantial
action to promote recreation develop-
ment. A more complete discussion of
the Act and the implementation of
Its provisions may be found in
Department of V/ater Resources Bulle-
tin No. 117, "Recreation and Fish
and Wildlife Program for the State
Water Project", 1968.
Recreation Financing
Lack of money poses the major
obstacle to recreation development
and the fulfillment of the State's
objective to provide its people with
the fullest possible recreational
opportunities. The seriousness of
the situation has been recognized
by the State Legislature which is
attempting to find ways and means
of meeting the problem. It is
generally recognized that it will
require the cooperative efforts of
governmental and nongovernmental
agencies alike. In spite of large
expenditures of funds by the govern-
ment and private sectors in the
past, the need for recreational
facilities remains larger than the
supply.
This "dollar shortage" has necessi-
tated a critical review of the state
program for the planning and develop-
ment of recreation and fish and wild-
life enhancement facilities in
connection with the State Water
Project. A task force was appointed
by the Secretary for Resources of
California's Resources Agency to
study this problem, and its findings
and recommendations have been pub-
lished in the "Report of the Recre-
ation Task Force on the State Water
Project", August I967. Further
-52-
discussion on this matter appears
in Department of Water Resources
Bulletin No. 117.
The State Electorate on November 3j
1970 approved an amendment to the
Davis-Dolwig Act which provides for
a total of $60 million in general
obligation bonds to finance the
design and construction of recre-
ation, fish and wildlife enhancement
features for the State Water Project —
$5^ million to be allocated to the
Department of Parks and Recreation
and $6 million to be allocated to
the Department of Fish and Game and
the Wildlife Conservation Board. To
carry out this program, the legis-
lation created a Recreation and
Fish and Wildlife Enhancement Com-
mittee consisting of the Governor or
his designee, the State Controller,
the Director of Finance, the State
Treasurer, and the Secretary for
Resources .
Design and construction of recreation
facilities at the State Water Proj-
ects will be implemented by the
Department of Parks and Recreation.
It is estimated that these water-
oriented recreation facilities
built In the next 5 to 7 years will
provide for an additional I6 million
recreation visitors. Activities to
be provided for Include boating,
fishing, water skiing, camping,
picnicking, riding, hiking, sight-
seeing', and swimming.
The $6 million specifically allo-
cated to fish and wildlife enhance-
ment includes the expansion of fish
hatcheries for production of trout
and warmwater fisheries, and the
provision of angler access to fish-
ing waters which has a potential of
realizing millions of recreation
days.
Some 17 reservoirs and more than
500 miles of canals and streams will
benefit from the "Recreation and
Fish and Wildlife Enhancement Bond
Act Program". The tentative
schedule for development in the next
5 years is to expend $8 million on
facilities in Northern California,
$4.5 million In Central California,
and $42 million in Southern California.
The Legislature has declared that
state costs for enhancement of fish
and wildlife and recreation should
be nonreimbursable as distinguished
from other water project purposes
which must be repaid by the water
and power users. Furthermore, plan-
ning, land acquisition, and the
Joint project costs allocated to
recreation are repaid to the extent
available from tidelands oil reve-
nues. Such repayment is limited to
$5 million per year.
Because of the magnitude of recre-
ation expenditures and allocations,
the Department expects the full
$5 million of reimbursements to be
required each year for the fore-
seeable future. In the long run,
the Department's expenditure of
funds for recreation will be repaid
In full. But there is a delay
between actual outlay and repayment.
When funds are in short supply, as
they have been in recent years, such
a delay puts a tight squeeze on the
availability of project funds,
intensifying the financing problem.
Solution of the financing problem
will not come easy or without cost
to the user. The implications of
the projected demands for recreation
suggest that annual expenditures
over the next 20 years should in-
crease sevenfold over present levels,
This allows for Just the Increase in
demand and does not include making
up deficiencies that now exist.
Fish and Wildlife Planning
Prevailing state and federal law and
policy (Water Code 233> Davis -Dolwig
Act, and P.L. 85-624, P.L. 89-72)
prescribe that fish and wildlife be
given full and equal consideration
with other project purposes In the
planning and design of water devel-
opment projects. These laws and
policies have evolved in realization
that the past role of fish and wild-
life interests in earlier water
development olanning, was largely
ineffective in implementing project
modifications in the Interest of pro-
tecting or enhancing fish and wild-
life resources.
-53-
Current planning efforts are direc-
ted toward assessment of the impact
of proposed water development proj-
ects on fish and wildlife, and the
recommendation of measures necessary
for preservation and enhancement of
these resources. Special attention
is being directed toward future
water needs for fisheries, and
measures necessary for the preser-
vation of wildlife habitat.
Streamflow Maintenance for Fish and
Wildlife: In addition to the water
reserved for wildlife management
areas shown in Table 4, various
governmental, public, and private
water and utility agencies have
entered into agreements with the
California Department of Pish and
Game to ensure adequate streamflows
and reservoir water levels to pro-
tect and improve fishery, wildlife,
and recreational values. Agreements
currently in force cover virtually
all the major developed watersheds
in California. It is most desirable
that these agreements be developed
early in the planning process so
that adequate steps may be taken to
ensure maintenance of water quality
in the project area and downstream
during project construction. Like-
wise, periodic review and revision
of flow schedules can improve proj-
ect operations and optimize flow
regimens in the interests of fishery,
wildlife and recreation. Table 6
lists current streamflow amounts by
hydrologic area to indicate the
extent of this important phase of
water project operations.
Existing agreements are as varied
as the watersheds they covero Mini-
mum flows may be for a stipulated
amount for a specified time period,
or adjusted flows may be called for
to raise existing flows to desirable
levels. Some stipulate the level of
water withdrawal from a reservoir
to bring downstream water tempera-
tures to optimum levels for spawning.
A few provide for hatchery water
supplies or spawning channels or for
TABLE 6
STREAMFLOV*
MAINTENANCE
AGREEMENTS
BY
HYDROLOGIC AREA
Annual
Water
Alloca
tions
for >
Streamflow Maintenance* |
Hydrologic Area
Sacramento Basin
[acre-feet)
3,900,
000
Delta-Central Sierra
14,
000
San Joaquin
258,
000
Tulare Basin
114,
000
North Coastal
677,
000
San Francisco
115,
000
Central Coastal
22,
000
North Lahontan
54,
000
South Lahontan
54,
000
*Water allocations shown are based
Dn
'normal
year"
runoff.
Actual releases may be
considerably
less where agreements |
provide for the alternative release
of
the natural
flow in
lieu of a stipulated fl
ow .
-54.
U.S. Bureou o( Reclamation
Sprinklers are becoming increasingly popular as a method lor improving irrigation efficiency
waterfowl management areas . Where
possible and desirable, certain flows
over and above those stipulated are
released to optimize spawning flows
for salmon and steelhead.
While streamflow maintenance agree-
ments have obviously alleviated
critical water shortages that would
have otherwise occurred in many
streams, water allocated for these
purposes, in some instances, has not
been sufficient to maintain fisheries
resources at satisfactory levels.
Turbidity, sediment, and temperature
problems have arisen under condi-
tions of controlled flows. Correc-
tive measures are being sought by
the State where such problems exist.
Fish and Wildlife and Recreation
Water Demands . The present and pro-
jected applied and net water demands
for recreation and fish and wildlife,
shown in Table 4, are for water used
in fish and wildlife management areas
and refuges, and that used consump-
tively by recreationists. In total,
the consumptive uses of water for
these purposes are comparatively
small, amounting to only 2 percent
of the 2020 state total water re-
quirements. However, in individual
areas, they can be very important
and create serious water problems.
Another very important demand for
water not reflected in the projec-
tions is the demand for water for
various environmental purposes, such
as water quality, fishery or recre-
ational enhancement, and instream
requirements for fish, wildlife, and
recreation.
The explosive growth in recreational
homesites throughout much of the
State is illustrative of impact of
-55-
man's activities on the resources of
an area, and the need for new local
water supplies. In the Tahoe Basin,
for example, the nonresident popu-
lation accounts for about three-
quarters of the area's water
requirements. In Nevada County, a
popular mountain recreation area,
it is estimated that 36,000 new
lots covering 48,000 acres have
been formed through subdivision
since 1964. When all of the exist-
ing lots are occupied, the treated
effluent discharge is expected to
exceed the normal minimum stream-
flows in the area. Major new water
supplies will have to be developed,
not only to meet domestic needs,
but also to maintain suitable water
quality standards in streams and
rivers where such development occurs.
Flood Damage Prevention
Despite extensive planning and con-
struction of flood control works
over a period of many years in
California, considerable flood
damage continues to occur as a con-
sequence of the State's continued
growth and occupation of active
floodplains .
All levels of government in the
State have assumed some degree of
responsibility in an effort to pre-
vent flood damage. Since the pas-
sage of the federal Flood Control
Act of 1936, however, the U. S. Amy
Corps of Engineers has taken the
lead in planning and constructing
flood control measures for major
basins with financial aid from the
State for the cost of lands, ease-
ments, and rights-of-way. Means of
mitigating urban flood drainage
problems have been left to the
resources of local agencies.
Examination of future flood control
needs in California conducted under
the Comprehensive Framework Study,
California Region, mentioned briefly
in Chapter II, indicates the 1965
average annual flood damage of
around $100 million will increase
to about $160 million by I98O if
no additional flood control measures
are implemented. This means that a
vigorous flood control program will
be needed to reduce these potential
future flood damages.
Despite a continued project-oriented
flood control program, the histori-
cal increase in flood damages sug-
gests a need to adopt a more bal-
anced approach to mitigating future
flood damage. This approach should
Incorporate more nonstructural
measures either as alternatives to,
where circumstances permit, or in
conjunction with structural
measures .
In this regard, the Cobey-Alquist
Flood Plain Management Act of 1965
mandates local government to regu-
late floodplain use within desig-
nated floodways prior to construc-
tion of economically justified
projects as a prerequisite to state
financial assistance in the cost of
lands, easements and rights-of-way.
When considering future flood con-
trol measures, greater attention
should be directed to desires of
the beneficiaries for environmental
enhancement. This suggests a
responsibility on the part of local
beneficiaries to become more in-
volved in the planning and selection
of such measures and in financial
participation where costs are
involved.
Water Quality
Water quality is an essential and
critical element of water resource
planning and management in Califor-
nia. Water of suitable quality
must be available in adequate
quantity at the times and places
needed for all intended beneficial
uses which may Include domestic,
industrial, agricultural, recre-
ational, fish and wildlife, and
other requirements.
Water Quality and Water Use
The term "water quality" has practi-
cal meaning only when associated
with specific beneficial water uses.
A suitable water supply is one which
-56-
satisfies water quality criteria
for the intended uses. Quality,
therefore, is inseparable from
quantity and must be evaluated along
with the purposes and uses for which
water supplies are developed.
Adequate planning for maximum use
and preservation and enhancement
takes into consideration the complex
interrelations of water quantity
and quality, of supply, use, and
disposal. Water systems are
dynamic . Changes in one part of a
water system may materially affect
other parts, whether those changes
are in the water or on the sur-
rounding land.
Water management and development
implies quality changes. The dams
on a river which are essential for
reliable water supplies also result
in a changed water environment,
such as different water temperatures,
alteration of turbidity, and changes
in aquatic habitat. Changes in land
use under different water use con-
ditions may alter the runoff pat-
terns and erosion characteristics.
Water use is clos
waste disposal,
contain not only
of the original s
trated form, but
added or properti
the use. Moreove
area may influenc
water supply to a
ely related to
The wastes often
the constituents
upply in concen-
also materials
es changed during
r, wastes from an
the quality of
downstream area.
The effects of water use and waste
disposal on the water resources may
be reflected in depletion of dis-
solved oxygen in streams and estu-
aries, toxic effects on aquatic
life, mineralization which renders
the supply unfit for further use,
and the m.ore subtle changes of
eutrophication. They can include
increased nitrates in ground water,
sea water intrusion, or compaction
of ground water aquifers by lower-
ing water levels .
Environmental changes may not be
detrimental. In fact, any water
resource management program is
designed to change the environment
for the benefit of mankind. The
major concern is to predict and con-
trol changes which will occur.
Municipal and Industrial Use. Water
for municipal supplies is used for
drinking, bathing, washing cars,
irrigating lawns, flowers and trees,
waste disposal, manufacturing pro-
cesses, and other purposes, some of
which may require special treatment
to meet particular needs. Drinking
water should be clear, colorless,
odorless, and pleasant tasting. It
must be free from disease-causing
organisms and other impurities which
endanger public health and should
not contain excessive amounts of
dissolved minerals. The most widely-
used guide, or criterion, for deter-
mining the suitability of water for
municipal use is the U. S. Public
Health Service Drinking Water Stan-
dards. These standards specify
limits for bacteriological, physical,
radiological, and chemical constitu-
ents in a water supply.
Industrial water supplies vary
widely in water quality requirements,
depending upon the types of indus-
trial processes involved. In gen-
eral, water suitable for drinking is
also suitable for most industrial
uses. Cost of treatment is an
important factor. Treatment costs
to soften hard water to desirable
levels may range from ^h to more
than $20 per acre-foot, depending
upon the use of water and the
method of softening.
Agricultural Use. Quality require-
ments for agriculture (irrigation)
depend upon many factors such as
crop types, so,il and drainage con-
ditions, climate, and irrigation
practices. Some crops are particu-
larly sensitive to certain constitu-
ents, especially boron.
Drainage of irrigated lands is of
major importance for continuing
successful irrigation. In irrigaticn
use relatively insignificant amounts
of dissolved minerals are consumed
in processes of evaporation and
plant growth, and salts are left
behind. Excess salts must be
-57-
leached from the soil and carried
off in drainage water. The content
of dissolved minerals in applied
irrigation water can have a signi-
ficant influence on the amounts of
irrigation water required for
leaching. In general, the lower
the total dissolved mineral concen-
tration in the water supply, the
lower the leaching water require-
ments. Also, the possibilities for
reuse of the return water are
enhanced.
Recreation. For recreational pur-
poses, clarity, color, temperature,
and bacterial quality are especially
important. The best quality of
water is needed for swimming and
other water contact sports. Bacte-
riological safety is of primary
importance for those activities.
General esthetics at water recre-
ation sites also may be affected
by water quality conditions. The
water must be protected from
obnoxious sights such as floating
oil, grease, foam and debris, and
from unpleasant odors. Levels of
turbidity, alkalinity and dissolved
oxygen must be held within desir-
able limits.
Fish and Aquatic Life. Water
quality considerations for main-
taining suitable environments for
fish and aquatic life include con-
trol of dissolved oxygen, tempera-
ture, turbidity, pH, and prohi-
bition of toxic materials or lethal
concentrations of trace constitu-
ents. Spawning or propagation of
fish also requires consideration of
bottom deposits and careful selec-
tion of temperature levels which
maintain optimum spawning conditions.
The aquatic environment has re-
ceived increased attention in
recent years because of the recog-
nition that accelerated changes in
the environment to meet population
needs can radically change the
habitat upon which fish, wildlife,
and the aquatic community are
dependent for their continued sur-
vival. Habitat is the collective
conditions in an area contributing
to the particular needs of an
animal for food, cover, space, and
reproduction. Each species has its
own highly restricted habitat needs.
Often the disruption of one small
but key element in the environment
can result in complete elimination
of desirable species.
Isolated occurrences of accidental
pollution such as oil spills or the
discharge of toxic materials into
receiving waters get most of the
publicity: and, of course, they are
cause fbr concern. However, chronic
pollution can occur without the
realization that harmful alterations
are taking place; and this In the
long run could cause more lasting
detriments to the aquatic environ-
ment. Changes caused by chronic
pollution may result in a "domino
effect" where the elimination or
change of one critical factor may
trigger a vjhole series of reactions
leading to the eventual destruction
of a healthy aquatic community.
Water Quality and Water Reuse
The quality of a water supply is
directly related to its reuse capa-
bility. A single cycle of domestic
use generally results in an Increase
of 100 to 300 parts per million of
dissolved mineral content. As pre-
viously noted irrigation return
water also becomes more saline than
the supply water. Therefore, in
terms of total mineral content,
water containing 100 to 200 ppm dis-
solved salts could successfully be
used and reused two, three, or even
four times, as compared to water
which Initially contains 700 to
800 ppm of dissolved salts, which
may not be used feasibly more than
once. Of course, reuse could also
be limited by the accumulation of
toxic materials or the presence of
individual mineral constituents even
though the total mineral concentra-
tion might be relatively low.
In the southern part of the State,
the Departmentof Water Resources is
engaged in a number of programs to
protect and conserve the quality of
-58-
Oroville Reservoir
High quality water is essential lor water contact sports
local water supplies and to encour-
age reclamation and reuse of waste
water for the ultimate purpose of
reducing the quantities of supple-
mental fresh water. These programs
range from monitoring and surveil-
lance of surface and ground water
and waste discharges, to working
with local water entities in the
formulation of plans and criteria
for conserving and improving ground
water quality, and developing plans
for ground water basin operation
and use.
Some areas in California contain
ground water that is virtually
unused because of its marginal or
brackish quality. Such is the case
in the Lower San Dieguito and Lower
San Diego River Valleys of San Diego
County. It may be possible to blend
this poor quality water with North-
ern California or other water sour-
ces to produce an acceptable water
supply at reasonable cost. By
Judicious operation of these ground
water basins it is also possible
that water quality might eventually
be so improved that the basins them-
selves could be used as storage
reservoirs .
term "beneficial uses" of California's
waters to include esthetic enjoyment
and the preservation and enhancement
of fish, wildlife and other aquatic
resources or preserves. Practically,
the addition of these beneficial
uses will enable more stringent
regulation of water use and waste
disposal to protect and enhance
water quality. Philosophically, the
inclusion of esthetic enjoyment and
enhancement of fish and wildlife is
a major departure from most existing
regulatory statutes. It recognizes
a new environmental awareness and
the growing public concern over the
water resources of California.
A most significant element of the
Water Quality Control Act provides
for development by the State Water
Resources Control Board of state
policy for water quality control and
regional water quality control plans.
"State policy" includes:
1. Water quality principles and
guidelines for long-range
water resource planning,
including ground water and
surface water management pro-
grams and control and use of
reclaimed water.
Water Quality Control
The State Water Resources Control
Board and the nine Regional Water
Quality Control Boards are the
principal state agencies with
primary responsibility for the coor-
dination and control of water
quality (VJater Code Section 13OOI).
The Department of Water Resources
is also mutually involved with the
water quality control agencies but
in a separate area of responsibility.
While the control agencies are
responsible for regulation of water
resources in a quasi- judicial sense,
the Department provides for develop-
ment and utilization of the resource
through planning and implementation
of physical works or management
techniques.
The new Porter-Cologne Water Quality
Control Act protects water quality
from both a practical and a philo-
sophical standpoint by expanding the
2. Water quality objectives at
key locations for planning
and operation of water
resource development projects
and for water quality control
activities.
3. Water quality control plans
adopted by the State Board
for interstate or coastal
waters or other waters of
interregional or statewide
interest .
4. Other principles and guide-
lines deemed essential by
the State Board for water
quality control.
The regional water quality control
plans for each hydrographic area of
the State encompass (l) the bene-
ficial uses to be protected,
(2) water quality objectives neces-
sary to ensure the reasonable protec-
tion of beneficial uses and the
-60-
prevention of nuisance, and (3) a
program of implementation and
enforcement .
These policies and plans become a
part of the California Water Plan
upon submission to the Legislature.
The Act also provides for regulation
of wastes which could affect the
waters of the State. Any person
proposing such a discharge, includ-
ing disposal of solid waste, must
file a report of discharge with the
appropriate regional board. That
board establishes, in accordance
with state policy and water quality
control plans, requirements under
which a waste discharge may be made.
The requirements may prescribe the
quality of the discharge, the effect
upon the receiving water, or both.
They may include a monitoring system
and a time schedule. The Board may
specify conditions on areas whei'e
no discharge is permitted. Viola-
tion of requirements may be abated
through board and court actions.
The violator may be subject to a
fine up to $6,000 for each day of
violation, or in the case of a
public sewage facility, may be pre-
vented from adding services to the
system until the discharge is in
compliance with requiremients .
Waste discharges into waters of the
State are privileges and not rights.
Thus, in addition to combining the
water rights and water quality
policy and regulatory functions Into
a single board, the Water Quality
Control Act strengthens and broadens
the integration of quantity-qual J ty
planning relations . It provides a
focal point through the California
V/ater Plan to ensure, in accordance
with the original precept of the
Plan, that the waters of the State
will serve the needs of the people.
As basic policy It provides that
activities which may affect the
waters of the State shall be so •
regulated to attain the highest
reasonable water quality levels, the
various needs to be met, and
related economic, social and other
considerations .
■61-
CHAPTER V. POTENTIAL WATER
SUPPLY SOURCES
California's water demands generally
have been met from traditional water
developments by storage and/or
diversion and transportation of
surface supplies, and extraction of
underground supplies. As the
State's economy has expanded, sur-
face water supply systems have
expanded from local developments to
large-scale systems involving
storage and long-distance conveyance
of water from intrastate and inter-
state streams.
However, rapidly advancing technol-
ogy has focused considerable atten-
tion on other possible sources of
water which are being studied
seriously as potential economic
water supplies. Most notable of
these are desalting of the inexhaust-
ible supply of sea water bordering
California's 1,200 miles of coast-
line, and reuse of reclaimed waters
instead of sewering them to the
ocean after a single use.
This chapter discusses various possi-
ble water supply sources which could
provide for increasing needs for
beneficial uses and purposes. It
covers development and transporta-
tion of additional surface water
supplies, the significance of ground
water and its relation to local and
imported surface water supplies, de-
salting, water reclamation, weather
modification, geothermal water,
watershed management. Western States
water development, and possible non-
structural alternatives.
The potential water supply sources
described in this chapter are not
presented in the sense of one alter-
native to be developed at the
exclusion of another. The antici-
pated rate of growth in California's
demand for water and water-related
services in relation to the various
potential sources of supply indi-
cates that a combination of the
water supply sources discussed may
well be required; and the selection
of that combination will be based on
the determination of how best to
schedule the development and use of
the various sources to effect the
optimal overall long-range satis-
faction of demands.
As we begin the 1970s, the accent on
environmental considerations requires
that a careful balance be maintained
between the preservation and protec-
tion of the water resource and the
development and use of that resource.
Moreover, as Indicated in Chapter IV,
the slowdown in growth of future
water demands In comparison with
earlier projections suggests that
more time is available for making
decisions regarding further conserva-
tion projects. These considerations
emphasize the need for maintaining
flexibility in the analysis and
choice of future options from among
the various alternatives.
Surface Water Development
While surface water resources are
ample to meet foreseeable statewide
needs on an overall basis, they are
maldistrlbuted geographically with
respect to the areas of need. For
example, about 75 percent of the
water resources occur north of the
Sacramento-San Joaquin Delta, while
some 75 percent of the requirements
occur south of the Delta. The geo-
graphical distribution of runoff
originating within the State is
illustrated in Figure 12.
About 60 percent of the total pres-
ent statewide applied water demands
is supplied from surface water
sources, comprised primarily of
local agency surface water develop-
ment, local agency imports, the
federal Central Valley Project and
other federal water developments.
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FIGURE 12
AVERAGE ANNUAL
FULL NATURAL RUNOFF
IN MILLION ACRE -FEET
HYDROLOGIC STUDY AREAS
- NORTH COASTAL
- SAN FRANCISCO BAY
- CENTRAL COASTAL
- SOUTH COASTAL
- SACRAMENTO BASIN
- DELTA- CENTRAL SIERRA
- SAN JOAQUIN BASIN
- TULARE BASIN
- NORTH LAHONTAN
- SOUTH LAHONTAN
- COLORADO DESERT
-64-
Imports by local agencies include
the Hatch Hotchy, Mokelumne,
Los Angeles and Colorado Aqueducts.
The "other federal water develop-
ments" category Includes imports
from the Colorado River for irri-
gation in the Imperial and Coachella
Valleys. The local surface water
developments will be specifically
identified in Chapter VI which will
present a comparison of demands and
supplies on a regional basis. A
number of existing and possible
local and major projects are shown
on Plate 1.
The potential for major additional
development of water supplies in
California is for the most part
limited to the Sacramento Basin and
the North Coastal regions. In the
other regions the available surface
supplies from the principal river
systems will have been largely
developed by existing reservoirs or
by those presently under co-is truction.
The potential remains for many
localized surface water develop-
ments on the smaller streams.
However, as with major develop-
ments, opportunities for such
developments occur primarily in the
North Coast and Sacramento Valley,
with limited potential in the North
San Francisco Bay area and the
Central Coastal area.
In addition to on-stream develop-
ment, a further conservation of
surface water resources could be
provided through the development of
off -stream storage facilities within
the Central Valley Basin. Off-
stream storage consists of a diver-
sion from a stream and conveyance
to a storage site where adequate
capacity is available. San Luis
Reservoir on the west side of the
San Joaquin Valley is an excellent
example of an off -stream storage
facility. Such reservoirs have
been proposed in connection with
the V/est Sacramento Canals Unit
(Sites Reservoir); the East
Side Division (Montgomery and
Hungry Hollow Reservoirs); and the
Delta Division (Kellogg Reservoir)
of the Central Valley Project.
Investigations have already been
made of the possibility of construc-
ting additional off -stream storage
sites at locations along the align-
ment of the California Aqueduct to
complement that presently provided
at San Luis Reservoir. Potential
storage facilities could be located
at the Los Banos site in western
Merced County or the Sunflower site
in Kings County.
Sacramento Valley Development
Potential
Two major streams with potential for
storage remain in the Sacramento
Valley. These are Cottonwood Creek,
the largest remaining unregulated
tributary of the Sacramento River,
and the Ihomes -Stony Creek system.
The Corps of Engineers has proposed
two reservoirs within the Cottonwood
Creek Basin at the Dutch Gulch and
Tehama sites. These storage facili-
ties could provide a high degree of
flood protection and a new water
supply of some 260,000 acre-feet
annually for local and statewide
service. The two reservoirs could
also provide fisheries enhancement
through control of the flows in the
principal spawning areas of the
Cottonwood Creek Basin located down-
stream from the damsites.
The Bureau of Reclamation has investi-
gated a reservoir development at the
Paskenta-Newville site on Thomes and
North Pork Stony Creeks. This poten-
tial facility could develop a new
water supply of as much as 300,000
acre-feet annually if coordinated
with existing features of the Central
Valley Project and the State Water
Project.
Additional large storage could also
be provided on Stony Creek at the
Rancheria site. Rancheria Reservoir
has been studied by the Department of
Water Resources both as an indepen-
dent project and as a part of a
Middle Fork Eel River development.
Rancheria Reservoir also has potential
for development of an economical addi-
tional vater supply by a pump- storage oper-
ation, with a diversion of Sacramento
River floodflows. Studies of the
-65-
n^imm^
San Lui.-5 Kcocfioir — — an c\cimpU- ut ull-^treaiii .^lur-if^i.-
latter possibility are in progress.
North Coastal Area
Development Po"te"ntial
The long-term mean annual runoff
from the large river basins in
northwestern California is approxi-
mately 27 million acre-feet, most
of which is unregulated. Prior
Department studies have indicated
that a physical potential exists
for the development of a total
dependable water yield within the
North Coastal region of up to 10-12
million acre-feet annually. Those
studies have also indicated that
such development could be adverse
to fisheries and wildlife resources,
particularly in relation to the
construction of large storage
facilities within the lower Klamath
River Basin.
Other problems of an environmental
and ecological nature may also be
created by traditional surface water
development through reservoirs with-
in the Klamath River Basin and else-
where in the North Coast. The
Department and the federal water
agencies are well aware of these
problems and of the need for more
sensitive analysis of the conse-
quences on the ecology and environ-
ment of future surface water devel-
opment within the North Coastal
area.
Within the upper Eel River Basin
two major developments have received
considerable study since I965.
These are the English Ridge Project
on the upper main Eel River, investi-
gated by the U. S. Bureau of
Reclamation, and the Dos Rios Proj-
ect on the Middle Pork Eel River
which was proposed for authorization
in 1968 by the U. S. Army Corps of
Engineers . The Dos Rios Reservoir
-66-
proposal generated considerable
controversy, particularly because
of the inundation of Round Valley
in Mendocino County, and the
necessity of relocating the com-
munity of Covelo and the local
Indian population.
In 1969 Governor Reagan expressed
his concern for these displacements
and directed the Department of
Water Resources to work with the
Corps of EIngineers to develop
further information on alternatives
to the proposed large Dos Rios
Reservoir. These alternatives to
the Dos Rlos Project, involving I6
project configurations, are pre-
sented in the Department's Bulletin
No. 172 entitled "Eel River Develop-
ment Alternatives", December I969.
The U. S. Bureau of Reclamation is
engaged in a reconnaissance-level
study of possible project configu-
rations within the lower Trinity
River Basin. The study also in-
cludes consideration of possible
diversions from the Mad and Van
Duzen Rivers to the Trinity River
system. The work to date has been
concentrated on three reservoirs --
Eltapom Reservoir on South Fork
Trinity and Helena and Schneiders
Bar Reservoirs on the main stem of
the Trinity River.
Very preliminary studies are also
being made by the Bureau of Recla-
mation of plans for direct diver-
sion from the Klamath and Trinity
Basins. Such plans would avoid the
need for main-stem reservoirs on
the Klamath and Trinity Rivers and
would appear to be the least dis-
ruptive to the fisheries and wild-
life environment. Holdover storage
would be provided in the Sacramento
Valley. These direct diversion
possibilities would involve extremely
large tunnels and would be more
costly than the previously examined
on-stream storage plans. However,
they could possess certain advan-
tages from the standpoint of main-
taining the Trinity-Klamath River
systems more nearly in their natural
environment, while at the same time
conserving the floodflows for con-
sumptive use purposes in other
regions of California.
Ground Water Development
Use of ground wa
began about I87O
Coastal area whe
approximately 10
drilled. Since
century, use of
resources has sp
State and now pr
40 percent of th
of the State.
ter in California
in the South
re, by I9OO,
,000 wells had been
the turn of the
underground water
read throughout the
ovides about
e total water needs
Continued and extensive use of this
vast resource has not been without
effects, the most apparent of which
are increased pump lifts and the
"drying up" of some surface streams
and ponds and swampy areas. Less
obvious are sea water intrusion
into coastal aquifers, migration to
wells of sea water entrapped inland
from earlier geologic periods, and
local subsidence of some land sur-
faces. In addition, legal actions
associated with ground water use
have occurred.
The characteristics of a ground
water basin must be deduced from
well water level measurements, well
logs, and other hydrologlc and
geologic data. This is a lengthy
and costly process which frequently
has led investigators to recommend
a decrease in ground water pumping
to stabilize pumping llfts--or to
import supplemental surface water
supplies, without fully understand-
ing the storage and transmissive
potential of underground aquifers.
However, the successes realized
from such actions have demonstrated
that ground wq.ter resources are,
indeed, subject to deliberate
planned management to achieve a set
of established goals.
Availability of Ground Water
Ground water can be obtained in
many areas in California. Produc-
tion varies from a few gallons per
day to several thousand gallons per
minute. Interest of the Department
of Water Resources has been directed
-67-
FIGURE 13
THE RESOURCES AGENCY
DEPARTMENT OF WATER RESOURCES
AREAS OF GROUND WATER
OCCURRENCE
LEGEND
ALLUVIAL FILL AREAS /^^
AREA OF VOLCANICS
"m>
\
-68-
to those areas in which ground water
is a significant water supply source.
Recent alluvial material (the valley
fill areas of the State) provides
the most prolific areas of occur-
rence of ground water. Alluvial
fill areas and other areas of occur-
rence of ground water are shown in
Figure 13. Most ground water
studies have been made in these
areas. Older alluvial materials
which frequently underlie and are
adjacent to the recent alluvium
have also been studied where they
are significant producers of ground
water.
Measures of the availability of
ground water include (l) annual
natural replenishment or recharge
(a measure of the annual yield),
which is generally about half the
permissible sustained pumpage; (2)
total storage capacity, a relatively
small portion of which is used to
develop the annual yield; (3) total
water in storage, which measures
the magnitude of possible extraction
of ground water in excess of annual
yield; and (4) usable storage capac-
ity, which indicates the portion of
total storage capacity usable in
conjunction with surface storage to
develop a reliable system yield.
The measures of availability of
ground water in known ground water
basins are summarized by regions in
Table 7 .
TABLE 7
3R0UND WATER IN CALIFORNIA
(1,000
Acre-Feet )
Region
Known Ground Water Areas |
Storage
Capacity
Water
in Storage
: Annual ,
: Primary^./
: Recharge
Total
: Usable
North Coastal Area
2,000
700
2,000
150
San Francisco Bay Area
3,000
1,100
1,000
310
Central Coastal Area
20,000
7,600
18,000
730
South Coastal Area
100,000
7,000
95,000
900
2/
Central Valley Area—
608, 000
102,000
540,000
2,760
Lahontan Area
157,000
700
100,000
190
Colorado Desert
Total
158,000
1,048,000
3,600
122,700
100,000
60
856,000
5,100
1/ Includes natural recharge plus recharge from local reserve
operated to augment natural stream channel percolation.
irs
2/ Combined areas of Sacramento Basin, Delta-Central Sierra area,
San Joaquin Basin, and Tulare Basin.
-69-
The table Indicates a total state-
wide ground water storage capacity
of more than 1 billion acre-feet.
This estimate is compiled from pub-
lished data based on varying depth
criteria, ranging from 200 feet in
the Sacramento Valley to 1,000 feet
in other areas, except where /
limited by the occurrence of saline
water or by non-water-bearing
materials. The table also indi-
cates that more than 800 million
acre -feet of ground water is in
storage. These large values are
in a sense academic, as they do not
represent a measure of availability
of the ground water resource. Sub-
stantial withdrawal from the 800
million acre-feet of ground water
in storage is analagous to the
mining of oil or natural gas re-
serves, as it would not be replen-
ished.
The two items of most significance
in Table 7 are the usable ground
water storage capacity and the
annual primary recharge. Usable
capacity, totaling about 123
million acre-feet, is only a frac-
tion of total storage capacity.
This estimate has been developed
from studies of varying intensity.
Limitations of usable storage
capacity reflect economic, legal,
quality (such as sea water Intrusion
into coastal basins), and other
constraints. Further, more detailed
studies are needed for refinement
of estimates of usable ground water
storage capacity in the individual
major ground water basins, taking
into account the various constraints.
The annual primary recharge shown
in Table 7 Includes natural ground
water replenishment under present
conditions and the recharge accom-
plished by operation of local reser-
voirs for detention and gradual
release of water to augment natural
stream channel percolation. It
does not Include the incidental
recharge resulting from the distri-
bution and application of surface
water supplies, which is considered
reuse. Such incidental recharge is
substantial, and will become more
significant in the future as greater
amounts of surface water supplies
are used. In addition, recharge
from deliberate spreading of local
and Imported water will increase.
Ground Water Management
Management of a ground water basin
Involves the planned use of ground
water storage in conjunction with
local and Imported surface water
supplies to effect the most econom-
ical use of total available storage
in meeting overall water demands.
Such management requires deliberate
augmentation of recharge to place
necessary quantities of water under-
ground, which necessitates planned
extraction patterns and facilities
to control internal transmission.
It also will necessitate measures
for protection of the ground water
resource from degradation from
accumulation of salts, sea water
intrusion into coastal aquifers, or
from pollution.
Increased ground water basin re-
charge often will require the use
of additional storage capacity.
Thus, while ground water replenish-
ment is a most important resource,
the availability of usable storage
capacity, which can provide regu-
lation to both local and Imported
water supplies to develop additional
yield, is an equally valuable
resource.
The use of ground water storage
capacity can be divided into three
general categories which relate to
certain areas of the State.
In water-deficient areas, such as
Southern California and the San
Francisco Bay area, ground water
storage capacity may be required to
provide terminal regulation to
Imported water supplies. In this
case ground water storage capacity
provides regulation of uniform
deliveries to varying monthly demand
schedules.
In the San Joaquin Valley, ground
water storage can be used to provide
regulation of surplus water Imported
-70-
from Northern California during wet
years for later local and possible
export use during subsequent drier
periods, thus complementing off-
stream surface reservoir storage.
In the Sacramento Valley, ground
water storage capacity similarly
could be operated in conjunction
with surface storage facilities.
This would allow some additional
storage of flood waters with an
increased firm water yield to meet
local and statewide needs.
With regard to augmentation of re-
charge, planned ground water replen-
ishment has been practiced on a sub-
stantial scale for a number of
years . The spreading of water by
the Los Angeles County Flood Control
District in the Montibello Forebay
in coastal Los Angeles County is a
notable example of such operation.
The principal areas of deliberate
recharge on a large scale are the
South Coastal area, San Joaquin
Valley, and the Santa Clara Valley
south of San Francisco Bay. Spread-
ing basins, pits, and modified
channels are the principal methods
of placing water underground.
Prevention of sea water Intrusion
is an essential management element
in coastal ground water basins.
Tills involves the operation of a
hydraulic barrier to create a sea-
ward gradient along the coast. This
gradient can be established by
injection of fresh water into the
aquifer, such as is being accom-
plished in the Los Angeles Coastal
Plain by the Los Angeles County
Flood Control District; a combined
injection-pumping extraction system,
such as is being employed at the
Alamitos Gap by the Orange County
Water District and the Los Angeles
County Flood Control District; and
a ground water extraction barrier,
such as constructed on an experi-
mental basis in the Oxnard Plain
near Ventura by the Department of
Water Resources.
During the early 1960s the Depart-
ment of Water Resources developed a
ground water model which permitted
studies of the integrated use of
surface and ground water facilities
by providing information enabling an
economic comparison of a range of
alternative plans. The computer-
ized model has been and is being used
in a number of cooperative ground
water basin management studies
jointly funded by the Department and
local agencies. The purpose of the
studies is to provide a basis for
local agency selection and imple-
mentation of the most advantageous
plan.
Such studies are being used by local
agencies to determine questions of
zones of benefit (Kern County),
benefits of possible modification of
classic court decrees for ground
water operation (Raymond Basin),
optimization of a water distribution
system (San Bernardino Valley
Municipal Water District), and
selection of a ground water storage
system rather than a dam and reser-
voir for regulation of imported
water (San Diego County).
The delivery of water from the State
Water Project aqueduct will provide
an opportunity for an additional
application of ground water manage-
ment practices. It involves the use
of excess aqueduct capacity during
the earlier years to deliver surplus
water for recharge and storage under-
ground as a reserve to meet future
Increased needs. Examples of such
practices are indicated in the
operations presently being conducted
in Santa Clara and Alameda Counties
in the San Francisco Bay area, in
the San Joaquin Valley, and in San
Bernardino County and the San Gabriel
Valley in the South Coastal area.
Such an operation could enable the
deferral of capital investment for a
subsequent water supply facility.
The foregoing ground water management
possibility is the opposite of
practices of the past, wherein vigor-
ous economies have developed by con-
tinued ground water overdraft,
thereby developing a financial base
for construction cfan importation
project. Carefully planned over-
draft of a ground water basin could
be practiced until a supplemental
water supply could be made available.
However, this could be only an interim
-71-
measure, as an additional water sup-
ply would be necessary to sustain
the economy and provide for future
growth.
Future Ground Water Use
The widespread availability of ground
water in California and the increas-
ing cost of the development of sur-
face sources suggest a larger role
of ground water in the future.
However, a number of physical,
economic, legal, legislative, and
political factors must be identified
and resolved before broad-scale
planned management can be realized.
Management of ground water resources
within the framework of an adopted
management plan requires that the
local agency be able to: (l) use
ground water basin storage capacity
to regulate local or imported sur-
face waters; (2) take steps to con-
trol sea water intrusion in coastal
areas; (3) regulate extraction
patterns; (k) finance needed facili-
ties; and (5) distribute benefits
equitably. Procedures are already
available for distribution of the
annual yield of the ground water
basin.
Some local agencies have powers to
create hydraulic barriers to sea
water intrusion, but no local agency
has the power to control extraction
patterns, except as accomplished
through the economic pressures of a
pump tax. A variety of financing
measures, from direct taxation to a
tax or assessment on water pumped,
are available to local districts.
In the future, financing methods
and a method of distributing bene-
fits could evolve into a single
financial system accomplishing both
purposes .
Finally, California's statutes are
not clear regarding ownership of, or
rights to, the use of ground water
storage capacity. The only laws and
regulations In this regard are those
established by the courts as prob-
lems have arisen and suits have been
filed by the aggrieved. A constitu-
tional amendment might be necessary
to define the right to withdraw
water that has been conserved through
use of this storage.
Agencies that are operating artifi-
cial recharge projects at this time
record the amounts of water placed
In storage as a basis for later
withdrawal, but no legal basis
exists for such withdrawal. Little
has been done to determine the
losses connected with use of under-
ground storage, or the apportionment
of losses among those agencies using
storage capacity. There have been
a number of proposals for a permit
or license system to use underground
storage, but no proposal is univer-
sally supported.
In summary, ground water in storage
and ground water storage capacity
constitute an extremely valuable
resource at present and will con-
tinue to be in the future. The
value of ground water resources lies
in the use of ground water in stor-
age and underground storage capacity
(l) to provide regulation of natural
replenishment, and (2) operated
coordlnatedly with both local and
imported surface supplies, to effect
the most economical use of total
available storage, both surface and
underground, as an Integrated sys-
tem. Full realization of such inte-
grated surface water-ground water
system operations in areas where the
ground water resource is available
will require legal and legislative
action and social and political
acceptance.
Desalting
Desalting is undoubtedly the most
talked-about potential source of
water supply to meet future needs
not only in California but also in
other areas of the Nation and the
world. The prospects for desalting
depend considerably on one's point of
view. In some arid regions of the
world adjacent to the ocean,
literally the only alternative to
desalting is water delivered by
barge. In such areas the art of
desalting has been practiced for
many years . Many of these
-72-
Installations have very small capac-
ities, and relatively large-capacity
plants were ordered only recently,
during the 19dOs .
In California, with an abundant
water supply from surface and
ground water, desalting has played
essentially no part to date in
water development. From the stand-
point of economics it is not con-
sidered that desalting will play a
significant role in supplying sub-
stantial quantities of water in
California much before the turn of
the century. Large -capacity de-
salting is expected to be by that
time a technical alternative and,
possibly, an economical alternative
to other water supply sources,
particularly in coastal areas.
Already, however, existing or
planned coastal cities with a popu-
lation of up to 50,000 and isolated
inland communities could be provided
with a supply of high quality de-
salted water from commercially
available apparatus at costs accept-
able for municipal and industrial
uses. The subject of desalting has
been reported on in depth in the
Department's Bulletin No. 134-69,
"Desalting--State of the Art".
Department's Desalting Program
The Department of Water Resources
has had a program in desalting
since 1957. Close cooperation has
been maintained with the federal
Office of Saline Water in an attempt
to develop and expand desalting
technology. The Department was
authorized to cooperate with the
Office of Saline Water, and the
California Legislature appropriated
funds for a 50-50 sharing of capital
costs for the federal Office of
Saline Water Demonstration Plant at
Point Loma in San Diego. The State
of California contributed about
$820,000 to the project during its
construction. After the United
States moved the plant to Guantanamo
Bay in Cuba, California, by mutual
agreement, transferred its interest
in the Point Loma plant to the
Office of Saline Water test facility
in San Diego.
Under provision of the Cobey-Porter
Saline Water Conversion Law desalted
water from this test facility is
delivered to the City of San Diego
through a pipeline constructed by
the Department of Water Resources.
The desalted water is used in the
San Diego area. By the end of fiscal
year I969-7O the Department had de-
livered over 650 million gallons
(2,000 acre-feet) of desalted water.
In addition to gaining experience
from handling the desalted water,
the Department is gaining experience
regarding the effect of desalted
water on various materials and
coatings from the study of 10 differ-
ent test sections in the pipeline.
In furtherance of its cooperative
efforts in areas of mutual interest
with the Office of Saline Water, the
Department of Water Resources updated
on November 17, I969 its 1958 coop-
erative agreement for mutual assis-
tance in the development and appli-
cation of desalting. Under the
current agreement the Department
will intensify its cooperative
efforts in the development of poten-
tial desalting applications and
sites, and in the development of a
large -capacity prototype desalter.
One of the early efforts will be to
explore thoroughly the possibilities
for the construction and operation
of a prototype desalter in Califor-
nia. Toward that end the Department
signed an agreement with the Office
of Saline Water on May 1, 1970 to
undertake a siting study for a
prototype desalting plant.
The prototype desalter program is
intended to develop a desalting
plant with a nominal capacity of up
to 50 million gallons per day (equi-
valent to 50,060 acre-feet per year).
The exact capacity will be a balance
between the need for technology and
the market for the desalted water.
Several years will be required in
the selection of a water service area
and a site; in obtaining authoriza-
tion; and in the design and construc-
tion of the plant.
This program Is needed in the 1970s
to develop large-capacity desalting
technology so that operating and
-73-
cost information can be available
for decision-making purposes in the
1980s concerning the role desalting
may play in meeting some of
California's future water require-
ments. Specifically, the program
is intended to accomplish:
1. Determination of technical
and operating information
from a prototype desalter
needed for the design and
cost estimate of large-
capacity desalters;
2. Operation of a prototype
desalter in conjunction
with an electric generation
unit to evaluate interface
problems between water and
power production;
3. Utilization of the water In
a water service area in
order to gain experience in
the best means of integrat-
ing a supply of desalted
water with other water
supplies ;
4. Establishing means of environ-
mentally acceptable operation,
especially in connection with
the discharge of warm sea
water and brine back into the
ocean.
Federal Desalting Program
Since congressional enactment of the
Saline Water Act in 1952, the
Federal Government has been actively
developing desalting technology. The
Act provides for the development of
practicable low -cost means of pro-
ducing water of a quality suitable
for various beneficial uses on a
scale sufficient to determine the
feasibility of production and distri-
bution on a large-scale basis. The
term saline water includes sea water,
brackish water, and other mineral-
ized or chemically charged water.
Federal expenditures for desali-
nation were modest until the mid-
1960s when a large expansion was
made in the program. Expenditures
during; fiscal year I969-7O were
about $25 million. The larger
budget has permitted the federal
Office of Saline Water to substan-
tially expand the reserach and de-
velopment work it can support.
Current Status and Cost of
Desaltirig
The aggregate capacity of desalters
on a worldwide basis has increased
from 60 million gallons per day in
1961 to about 310 million gallons
per day at the start of 1970, for
an annual growth rate of 18 percent.
The total desalting capacity by 1975
is projected to increase to 1,250
million gallons per day.
Prior to 1967 the largest single-
unit sea water desalter had a capa-
bility of producing about 1.7
million gallons per day (1,700 acre-
feet per year). In I967 a desalter
was placed in operation in Key West,
Florida, with a capability of pro-
ducing 2.6 million gallons per day
(2,600 acre-feet per year) in a
single-unit plant. The Key West
plant desalts sea water for about
85 cents per 1,000 gallons, or $280
per acre-foot. It was the largest
in the world until late 1968 when a
plant was completed at Rosarito
Beach, Mexico. It has a capability
of 7.5 million gallons per day
(7,500 acre-feet per year) from
twin-unit desalters, each with a
capacity of 3-75 million gallons per
day. Desalted water from the
Rosarito Beach plant has been esti-
mated to cost in the 65-to-75-cents-
per-thousand-gallon range ($210-245
per acre-foot).
In 1969 Kuwait purchased five desalt-
ing units, each with a capacity of
6 million gallons per day for a
total capacity of 30 million gallons
per day. These plants are expected
to be placed on the line starting in
1971. The projected cost of desalted
water from the 6-million-gpd plants
is expected to be about $100 per
acre -foot. However, in Kuwait the
cost of fuel is only about one-tenth
the cost in California.
-74-
studies and plans are under way in
many countries for much larger de-
salting plants, usually in combina-
tion with power production. A
nuclear reactor is the most likely
energy source for these very large
plants.
One of the most complete studies
for determining the probable cost
of desalted water in large-capacity
plants was the Bolsa Island Project,
a dual-purpose nuclear power and
desalting plant, studied by the
Metropolitan Water District of
Southern California, local power
utilities, the U. S. Office of
Saline Water, and the U. S. Atomic
Energy Commission.
The desalted water from the Bolsa
Project delivered to the Diemer
filtration plant for distribution
was estimated in 1965 to cost $88
per acre-foot ($0.27 per thousand
gallons), and estimated in 1968 to
cost $143 per acre-foot ($0.44 per
thousand gallons). This project
did not proceed largely because of
escalation and the cost and uncer-
tainties associated with licensing
of the nuclear reactors.
Desalting in the Future
As the technology of removing
dissolved solids from water is de-
veloped and the cost of such proces-
ses is lowered, the economic feasi-
bility of supplying desalted water
to more areas of the State will in-
crease. It is anticipated that
developments in desalting will pro-
vide new and promising means to
assist in the future development of
California's water resources and
must be considered as an option in
the development of future water
supply sources.
Reduction in the cost of desalted
water from large -capacity plants of
the future can be achieved through
the application of nuclear energy,
most likely in dual-purpose plants.
However, nuclear desalters will
encounter the same licensing and
safety problems as will nuclear
power-only plants. A satisfactory
solution to siting on the California
coast will not be easy. Failure to
achieve resolution of the siting
problems may add materially to the
cost of desalting as an alternative
source of supply to meet future
needs in California.
At the present time the distillation
methods (the use of heat to boil
water) of desalting show the most
promise for large-capacity sea water
desalting. Developments have been
substantial with the reverse osmosis
process (the separation of water
from the salt solution by passage
through an organic membrane). It
seems entirely possible that con-
tinued developments in this tech-
nology could substantially widen
desalting options in the future in
terms of sea water, brackish water,
and waste water desalting and in the
flexibility of plant locations.
The distillation method of desalting
produces almost salt-free water.
This high-quality water would have
a value in "stretching" existing
supplies and in water quality
management in general . This poten-
tial exists in several areas of
California where the water supplies
presently available are slightly
brackish but could be made more
usable through a blending process.
Looking into the future, the expec-
tation is that the technology needed
to build dual-purpose nuclear sys-
tems could be developed so that con-
struction of large-capacity sea
water desalters might be initiated
in the mid-1980s for operation in
the 1990s. Also in the 1990 time
frame the reverse osmosis process
utilizing electro-energy may be
developed so that such desalters for
sea water and other salt waters,
including waste waters, can be
located close to the point of water
demand and at the same time at a
considerable distance from the
necessary power source. As larger
capacity facilities are built,
brine disposal problems will become
more f ormi dab 1 e .
Many factors that will Influence the
cost of desalted water In the future
-75-
cannot be determined with certainty,
Expectations, however, appear to be
sufficiently attractive to warrant
continued consideration of desalt-
ing as an alternative for future
augmentation or supplementation of
water supply.
Water Reclamation
The 2 million acre-feet of munici-
pal waste water discharged annu-
ally in California represents a
significant flow of water to be
considered in planning for future
water supplies. At the present
time less than 8 percent of this
waste water is reclaimed for bene-
ficial uses. Although certain
technical, economic and other fac-
tors would preclude renovation and
reuse of all waste water generated,
there would still be an Important
residual that could be put to bene-
ficial use, thereby stretching the
use of a primary water supply to
meet increasing water demands in a
region. Water reclamation also can
reduce overall waste disposal costs
and translate potential water
quality control problems into en-
vironmental enhancement.
Conditions are becoming increasing-
ly more favorable for water recla-
mation. Current emphasis on "clean
water", for example, necessitates
higher levels of treatment solely
for the purpose of waste water dis-
posal. Also the public is becoming
more receptive to the idea of water
reclamation and reuse. In consid-
ering the feasibility of water
reclamation as a potential source
of additional water supply, all
benefits, costs, constraints, and
other factors must be evaluated, as
Is done with any other potential
water supply source.
This section discusses the role of
the Department of Water Resources
and the potential and present status
of water reclamation In California.
The Department's Role in
Water Reclamation
In planning for water supplies to
meet future needs the Department of
Water Resources considers water
reclamation of significant potential.
Since 1952 the Department has col-
lected Information on waste treatment
facilities, quality and quantity of
major waste discharges, and waste
water reclamation projects in
California. At the present time an
inventory is maintained on the quan-
tity of significant waste discharges
in the metropolitan areas of the
South Coastal and the San Francisco
Bay areas .
This inventory serves as a basis for
more detailed studies of the feasi-
bility of waste water reclamation to
meet a part of the demand for addi-
tional water supplies. Data are
obtained on the quantity of reclaim-
able water, beneficial uses, and
costs of producing reclaimed water.
The objectives of such studies are
to evaluate the practicality of re-
claiming water from waste flows and
to encourage and stimulate the plan-
ned reuse of waste waters of suitable
quality, where warranted.
The Department considers three
general ways in which waste water Is
recovered for beneficial use: (l)
by discharging effluent into a
natural water course such as a river
or ground water basin, without
deliberately intending to reclaim the
water, (2) by constructing and oper-
ating facilities for the express
purpose of reclaiming water from
wastes, and (3) by directly putting
to beneficial use effluent from a
treatment facility intended primarily
for sewage disposal .
Water reclamation as defined under
item (l) occurs incidentally in
nonnal water use and waste water dis-
posal practices In Inland areas and
is not included in any estimates of
quantity or cost In this section.
Items (2) and (3), but primarily
item (2), deliberate renovation of
water, are of concern In this dis-
cussion. The major factors of con-
cern in deliberate renovation and
-76-
reuse of waste water are protection
of public health, concentration of
dissolved minerals, costs, and
public acceptance.
Most existing water reclamation
projects employ conventional sewage
treatment processes to remove objec-
tionable materials from the waste
water. For example, the secondary-
sewage treatment process, if proper-
ly designed and operated, can pro-
duce a clear, odorless effluent,
almost completely free of organic
and bacterial content. Additional
treatment, such as filtration and
disinfection, can ensure destruction
of most disease agents; however,
these processes produce very little
change in the mineral content of
the water. Reclaimed wateris not
used directly to meet domestic
water demands because of problems
of detection, identification, and
removal of virus and other disease
agents .
Potential Future of
Water Reclamation
The most favorable opportunity for
economical direct reclamation of
waste water appears to be in those
locations in the State where import-
ed primary water supplies are expen-
sive, and where large quantities of
water with low mineral content are
discharged to the ocean after only
one use. These conditions prevail
largely in California's South
Coastal and San Francisco Bay areas.
Moreover, the present national,
state and general public interest in
high levels of water quality impose
increasingly stringent waste dis-
charge requirements. Compliance
with these high standards will
necessitate expensive and more
advance treatment facilities whether
or not water reclamation is intended.
Any additional costs for reclamation
should be relatively small and this
should encourage a trend for more
waste water reuse.
In the Central Valley and other in-
land regions of California almost
all waste water is reused inciden-
tally. Quantities are taken into
account in planning for future water
supplies to serve these regions, but
are not identified specifically as
water reclamation. Also, agricul-
tural return flows are not con-
sidered as waste water in the context
of this discussion, as flows, for
the most part, are retained in the
water supply system and are avail-
able for reuse. Accordingly, they
are regarded as part of the avail-
able supply in the Department's
planning studies.
In the North Coastal region, water
supplies are basically plentiful:
therefore, the necessity for recla-
mation and reuse of waste water is
not considered of immediate impor-
tance. As in the Central Valley,
water is indirectly reclaimed where
waste water is returned to streams
and becomes a part of the downstream
water supply.
In evaluating the potential of water
reclamation a determination must be
made of the quantities of water that
can be feasibly reclaimed from waste
discharges in each area. Feasible
water reclamation may be defined as
the amount of water produced by the
waste water treatment process that
can be reclaimed and directly used
in an area to meet the economic
demand for water without causing
physical, economic, and public
health detriments. Feasible water
reclamation quantities are con-
sidered in the Department's water
supply projections and are based on
project feasibility studies. These
studies include consideration of
costs, demands for reclaimed water,
and physical constraints such as
ground water recharge capacity.
Quantities of waste water generated
in an area are directly proportional
to quantities of water supply. Con-
sumptive uses and system losses re-
duce the total quantity of municipal
waste water to about 30 percent of
the total municipal water supply.
The quantity of waste water that can
be feasibly reclaimed may be limited
by the quality of waste water, cost
of treatment, prospective uses, and
location of prospective use sites.
Also a certain amount of water would
still be needed to transport residual
-77-
wastes to the ultimate disposal site
such as the ocean. In general, not
more than about 20 percent of the
total municipal water supply in
coastal communities should be con-
sidered available for reclamation
on a practical basis.
Waste water containing total dis-
solved solids in excess of 1,000
parts per million generally is
unsuitable for most beneficial uses
and is not considered potentially
reclaimable at this time. Also,
the presence of specific chemicals,
such as mercury, arsenic, cyanide,
fluoride, boron, phenols, nitrate,
and sulfate, as well as other toxic
materials, could cause waste water
to be unsuitable for reclamation.
Additional research is needed on
detection, removal, and effects of
toxic materials in the water
environment ,
Although there are certain restric-
tions on its use, reclamation of
waste water is increasing in the
South Coastal area and other areas
where it can be put to beneficial
use locally. At the present time
the City of Los Angeles and the
Los Angeles County Sanitation
Districts dispose of approximately
700 million gallons of waste water
per day (780,000 acre-feet per year),
mostly through ocean outfalls into
Santa Monica Bay. However, there is
a trend toward constructing the new
waste water treatment plants farther
inland. This is more economical
than constructing long trunk sewers
and ocean outfalls. Also, rela-
tively inexpensive water supplies
become available to downstream areas
of use with little or no pumping
required.
The potential amount of water which
may be reclaimed from wastes in the
South Coastal area, where about
90 percent of the State's potential
lies, is estimated to increase from
110,000 to 1.1 million acre-feet
per year between 1970 and 2020.
This is shown in the tabulation at
the bottom of this page which also
Indicates that feasible reclamation
in that area could range from about
50,000 acre -feet per year at the
present time to 600,000 acre-feet
per year by 2020. The difference
between potential water reclamation
and feasible water reclamation, as
shown in the tabulation, could be
considered as a possible additional
supply to satisfy uses not included
in the projected water demands dis-
cussed in Chapters XV and VI.
In the future, uses for reclaimed
waste water undoubtedly will expand,
including uses for landscaping,
greenbelts, fire suppression, and
recreational lakes. In brushy areas
waste water could be used to reduce
fire hazards. On an Integrated
system basis, digested sludge from
the waste treatment plant could be
used as a soil conditioner and
fertilizer. Also, nutrients in
waste water are major fertilizer
ingredients and could be beneficial
in an irrigation water supply.
Present Status and Use
of Reclaimed Water
Figure l4 shows locations of all
coastal municipal waste water
1,000 Acre -Feet
Waste Water Production
Potential Water Reclamation
Feasible Water Reclamation
1970
: 1990
: 2020
1,225
1,960
2,700
110
760
1,100
60
300
600
-78-
FIGURE 14
j LOCATION AND RELATIVE QUANTITIES OF MUNICIPAL
WASTE WATER DISCHARGED IN COASTAL COUNTIES
OF CALIFORNIA
1968
NORTH COASTAL
SAN FRANCISCO BAY
CENTRAL COASTAL
SOUTH COASTAL
SACRAMENTO BASIN
DELTA - CENTRAL SIERRA
SAN JOAQUIN BASIN
TULARE BASIN
NORTH LAHONTAN
SOUTH LAHONTAN
COLORADO DESERT
WASTE WATER FACILITY WHICH DISCHARGES
MORE THAN ONE MILLION GALLONS PER DAY
-3 SCALE OF WASTE WATER QUANTITIES DISCHARGED
2 IN EACH COUNTY IN 100 MILLION GALLONS PER DAY
-79-
facilities which discharged more
than 1 million gallons of effluent
per day in I968. Also shown,
graphically, are total quantities
in 100 million gallons per day of
municipal waste water discharged in
each coastal county. The figure
illustrates the greater concentra-
tions of individual waste water
facilities as well as the greater
quantities of municipal waste water
discharged in the San Francisco Bay
and South Coastal areas.
A directory compiled by the Califor-
nia Department of Public Health in
1969 listed 172 water reclamation
projects either under construction
or in operation in California. The
directory included the use or uses
to be made of the reclaimed water.
Irrigation of agricultural crops,
principally fodder and pasture, was
carried out in 138 projects.
Present water reclamation in Cali-
fornia aggregates about 135^000
acre-feet per year with irrigation
as the major application. In I967
about 95*000 acre-feet of reclaimed
water was used to irrigate nearly
23,000 acres of land at various
locations. The following examples
cover some of the major types of
use.
At Golden Gate Park in San Francisco
reclaimed water supplies about 1
million gallons of water per day
(1,100 acre-feet per year) from the
middle of January through November
for use in the park's ornamental
lakes and irrigation system. This
source supplies about 25 percent of
the 1,017-acre park's water needs
for horticultural purposes.
The Whittier Narrows Water Recla-
mation Plant of the Los Angeles
County Sanitation District has
established the practicality of
large-scale planned ground water
replenishment operations using
reclaimed domestic waste water. The
facility reclaims 14 million gallons
per day (15,000 acre-feet per year)
of domestic sewage for downstream
ground water replenishment.
At Santee in San Diego County the
Santee County Water District oper-
ates a planned water reclamation
system of small lakes for recre-
ation. About 4 million gallons per
day of domestic sewage, after
secondary treatment and pond oxi-
dation, is pumped upstream to Syca-
more Canyon where effluent percolates
through the alluvium to collection
galleries for use in the recreation-
al lakes. Six lakes have been cre-
ated, four of which are used for
fishing and boating. Some of the
lake water is further treated and
used in a nearby swimming pool. A
park adjoins the lakes with picnick-
ing and playground facilities. Some
of the reclaimed water is used to
irrigate a nearby golf course.
The Indian Creek Project of the
South Tahoe Public Utility District
was also implemented because of a
need to dispose of waste water.
There were indications that nutrients
from waste water discharged into
Lake Tahoe were stimulating the
growth of algae which could eventu-
ally destroy the alpine-blue color
of the lake. As a partial solution
to the problem waste water generated
on about one-half of the land sur-
rounding the lake is now given
advanced tertiary treatment in a
plant designed for 7.5 million
gallons per day and pumped out of
the basin into Indian Creek Reser-
voir in Alpine County. The water is
used for Irrigation in the downstream
Carson River drainage. Indian Creek
Reservoir also has developed an
abundance of aquatic life and the
beginning of what may turn out to be
one of the best fisheries in
Northern California.
Water Reclamation Studies. It was
mentioned earlier that the Depart-
ment has conducted studies of the
feasibility of waste water reclama-
tion in meeting a part of the demand
for additional water supplies.
Studies have been completed for the
San Francisco-San Jose area,
Watsonville area, Los Angeles metro-
politan area, coastal San Diego
County, Coachella Valley, and
Ventura County. A study Is now
-80-
Water Reclamation Projects
Santee Onv ol four lakt-s used lur iishing cind Ixxiling
.<r
South Tohoe Public Utility District
Indian Creek Reclaimed water supply to lake exceeds U.S. Public Health Service drinking wali-r slandardt^
under way in San Luis Obispo County.
Bulletins which have been published
to present the findings of the com-
pleted studies are listed below.
Unpublished reports or data on addi-
tional studies are available in the
Department's files.
1. Bulletin No. 67, "Reclamation
of Water from Sewage and
Industrial Wastes, Watsonvllle
Area, Santa Cruz and Monterey
Counties", 1959.
2. Bulletin No. 80, "Feasibility
of Reclamation of Water from
Wastes in Los Angeles Metro-
politan Area", I96I .
3. Bulletin No. 80-2, "Reclama-
tion of Water from Wastes :
Coastal San Diego County",
1968.
4. Bulletin No. 80-3, "Reclama-
tion of Water from Wastes:
Coachella Valley", I966.
Evidence exists that these programs
and reports have stimulated interest
in the reclamation of water from
wastes, particularly in Southern
California.
Cost of Water Reclamation. Costs
assignable to water reclamation are
a function of costs of water supply
and waste disposal and depend to a
large extent on pricing policies of
the agencies involved. In general,
the cost assignable to the reclama-
tion of waste water is the cost over
and above the cost of treatment for
disposal plus the cost of delivery.
In evaluating the cost of water
reclamation a major consideration is
that any costs for primary and secon-
dary treatment should be allocated
to waste water disposal because this
level of treatment is required for
disposal whether or not reclamation
occurs. For most uses waste water
receiving secondary treatment is
generally satisfactory, and the cost
of the reclaimed water is the cost
of delivery.
Water receiving no more than secon-
dary treatment can generally be
used for ground water replenishment
and controlled Irrigation. The
delivered cost of this water depends
on the capital cost of the trans-
mission facilities, the amount of
pumping required, and the quantity
of reclaimed water involved. For
existing reclamation projects, esti-
noated costs range from $5 to $20 per
acre-foot. Reclaimed water injected
Into wells for sea water intrusion
barriers must receive tertiary treat-
ment, including possibly coagulation
and sedimentation. This increases
the cost of the water by $15 to $20
per acre-foot. Estimated costs of
reclaiming waste water ranged up to
about $50 per acre-foot in several
feasibility reports prepared by
local agencies and to more than $100
per acre-foot for a small reclamation
project producing less than 1,000
acre-feet per year.
Legal Requirements and Public
Acceptance. Regulations and re quire-
ments for quality of water from all
sources that can be used by the
public have been set by state and
local authorities . To ensure protec-
tion of the public health, and other
social benefits, state and local
authorities impose stringent regula-
tions and requirements upon reclama-
tion of water from wastes. These
authorities include the State Depart-
ment of Public Health, the State
Water Resources Control Board, the
California Regional Water Quality
Control Boards, the State Department
of Fish and Game, and county and city
agencies .
Pursuant to the Water Reclamation Law
(Division 7, Chapter 7 of the Water
Code), the Department of Public
Health has promulgated a set of
standards for safe reuse of waste
water for specified purposes. The
regional water quality control
boards are empowered by this law to
apply these standards in setting
requirements for the reuse of re-
claimed waste water.
The renovation of waste water in the
past has generally met requirements
for the uses intended. In the future,
as the technology of reclaiming waste
-82-
water improves, water of even better
quality may be produced.
Reclaimed water has been used in
California for many years and the
public now appears to be more fully
accepting its use. As the costs of
new water supplies and waste water
disposal continue to rise, it may be
anticipated that the public will
react favorably to any project that
will reduce the cost of either or
both of these necessary services.
These factors, along with advances
in technology on reclamation, indi-
cate that planned reuse of reclaimed
water will become an increasingly
significant portion of the total
water supply in the South Coastal
area.
Western States Water
Development
Among the alternative sources of
water that should be considered in
planning to meet California's future
water needs is importation through
western states or international
water development. Such a develop-
ment might deliver water (l) near
California's northern border for
distribution via natural streams and
existing or new aqueduct systems in
the Central Valley and adjacent
areas; (2) near the eastern boundary
to serve portions of the area east
of the Sierra Nevada; or (3) to the
Colorado Desert and South Coastal
areas probably, at least in part,
through augmentation of and rediver-
sion from the Colorado River.
Other Possible
Sources of Water
The possibilities offered by new or
nontraditional sources of water are
intriguing. In general, the public
seems to be keyed to the potential
rather than the limitations of new,
economically unproved methods for
developing water supplies. This is
a proper public attitude, for such
an attitude is a necessary climate
for advancement in technology; but
it is also necessary that enthusiasm
for the potential be tempered by
knowledge of the physical, economic,
and social constraints so as to
enable valid comparison with other
alternative available sources.
This section discusses several possi-
ble sources of water which could
assist in meeting California's
future water demands. Among the
possible new sources are weather
modification, watershed management,
and geothermal energy for desalting
of saline ground water. New or
expanded concepts of long-distance
transportation of water are repre-
sented in an interstate transfer of
surplus water within the Western
States, and in a proposed undersea
aqueduct. Finally, the possibility
of stretching available water sup-
plies through reassignment of uses,
pricing policy, and greater efficiency
in water management is discussed.
Developments of this scale, involv-
ing importation from the North-
western States or even from Canada
or Alaska, would be of such magni-
tude that they would probably be
practical only in conjunction with
a general plan to augment the waters
of the Colorado River stream system.
The cost of such a development
would be very large and necessary
political arrangements would be com-
plex. Thus, it could be considered
only a possibility for meeting the
long-term needs of the State some-
time after the turn of the century.
It is widely recognized that the
Colorado River stream system is over-
committed by existing and authorized
projects and water uses under the
Mexican Water Treaty, the Colorado
River Compact, and related legal
documents. The insufficiency of the
Colorado River became well-known
during the lengthy U. S. Supreme
Court litigation in Arizona v.
California . The decree in that case
provided that California's annual
apportionment is 4,400,000 acre-feet
when 7,500,000 acre-feet of main-
stream water is available to the
lower basin states. California is
entitled to 50 percent of any sur-
plus water above 7,500,000 acre-feet.
In the event of shortage, the decree
provides that the Secretary of the
Interior may apportion the remaining
available supply. The Colorado
-83-
River Basin Project Act of I968
directed the Secretary to follow
certain specific priorities in the
event of shortage .
Soon after the Supreme Court opinion
in 1963, the Bureau of Reclamation
published a report describing its
^'Pacific Southwest Water Plan". The
chief proposal of this plan was to
import water to the Colorado River
from Northwestern California. In
presenting this report, the Secre-
tary made it clear that this plan
was only a proposal, and he invited
alternative suggestions. In re-
sponse to that invitation, and on
the basis of other motivations, a
total of about 22 proposals' were
made according to a report by the
Western States Water Council
entitled "A Review of Inter-Regional
and International Water Transfer
Proposals", dated June I969 • These
include not only possible diversions
from the Columbia and Missouri Rivers
systems to augment waters of the
Colorado River and other water supply
sources in the Southwest, but also
proposals to divert water from
Canada or from Alaska to meet needs
not only of the Southwest, but also
of the Great Plains area, portions
of Central Canada, and the Great
Lakes area.
While these proposals identified
possible future sources of water and
demonstrated various physical means
by which large quantities of water
could be moved, they were based on
very cursory Information. Little
attention was given to the highly
significant political, legal, insti-
tutional, and social factors. More-
over, potential economic demands for
water in the areas to be served were
not given real consideration, and
hydrologic and cost data were only
very rough approximations.
Information is now being accumulated
through state water planning studies,
federal Type I Framework Studies,
other studies under the aegis of the
federal Water Resources Council, and
by boards and agencies within Califor-
nia, which hopefully will provide a
foundation for more detailed studies
in the future, possibly involving
such large-scale plans.
The first westwide investigation was
authorized in Public Law 90-537, the
"Colorado River Basin Project Act"
of 1968 (discussed in Chapter II).
This act directed the Secretary of
the Interior (l) to determine the
water supplies available and the
long-range water requirements in
each water resource region of the
Western United States; (2) to develop
a reconnaissance general plan to
meet the future water needs of each
region, but within the limitations
of the 10-year moratorium (see page
page 15); (3) to continue to develop
a regional water plan to guide the
coordination and construction of
water projects in the Colorado River
Basin; and (4) to recognize the
Mexican Water Treaty as a national
obligation when the Colorado River
is augmented (see page 15).
This investigation is to culminate
with a final report by Jrly 1, 1977.
Following September 30, j--.'^, the
Secretary, under other authoriza-
tions, can proceed with examining
sources of supplemental water out-
side the area just described,
including the Pacific Northwest.
Beyond the need for augmentation of
Colorado River supply is the prob-
lem of increasing salinity in the
Lower Colorado River, which impairs
the usefulness of the water for
agricultural and other purposes,
both in the United States and in
Mexico. Thus, to both increase its
quantity and improve its quality,
augmentation of the Colorado River
will probably eventually come to
pass and provide a potential means
of meeting part of California's
future water demands.
Weather Modification
For centuries man has sought means
of making rain to end drought periods.
However, it has been only in the
last two decades that serious
research and experimentation have been
undertaken toward inducing rainfall
through cloud seeding. Research and
-84-
experimentation activities have also
been directed to clearing of fog
from airports and to suppression of
hail or lightning storms.
Considerable progress has been made
during the past several years in
advancing the state of the art of
weather modification; and it has
been demonstrated that, under
favorable conditions, precipitation
can be Increased on the order of
5 to 10 percent. The most common
method of seeding clouds is by the
dispersal of silver iodide either
from airplanes or from ground
generators .
During the 1968-69 season, 11
weather modification projects were
conducted in California, mainly to
Increase surface storage in reser-
voirs for municipal and irrigation
use and for electric power genera-
tion. Additional purposes were for
augmentation of ground water storage,
fog dispersal, and for applied re-
search. Silver iodide and dry ice
were the agents dispersed, except
for a project in San Diego County
which employed an electrical dis-
charge method.
Direct measurement of results of
weather modification activities so
far is impossible because of the
great variety in natural weather and
rainfall patterns, and the sometimes
conflicting evaluations; but certain
conclusions are becoming apparent.
It is evident that there are certain
conditions under which precipitation
can be increased by cloud seeding.
Evaluations, by the operators, of
results of cloud seeding in the
Kings River (by Atmospherics Incor-
porated) and San Joaquin River (by
North American Weather Consultants)
watersheds Indicate a relatively
high degree of confidence in average
increases of runoff of 6 and 8 per-
cent, respectively. Estimated
annual precipitation increases of
5 percent have been reported by
Pacific Gas and Electric Company for
the Lake Almanor watershed In the
Feather River Basin.
A weathsr modification project in
Santa Clara County has increased
average precipitation over the
watershed by an estimated 10 to
15 percent, as reported by the Santa
Clara County Flood Control and Water
District. A continuing weather mod-
ification program in the drainage
basins above the reservoirs of the
Los Angeles County Flood Control
District Indicated, according to
consultants, overall increases
ranging from near zero to 20 inches
during the eight -year period from
1960-61 through 1967-68. These
Increases, averaged over the entire
basin, have been estimated to be in
the neighborhood of 5 percent of
the mean annual precipitation.
The Office of Atmospheric Water
Resources, U. S. Bureau of
Reclamation, has stated that results
of Project Skyvjater and other pro-
grams in the United States and
abroad indicate that precipitation
can be increased by an average of
10 to 20 percent. This average
includes cases of large increases,
small Increases, no increases, and
some decreases. The foregoing
reference also reported that costs
for indicated increases in runoff
will range from $0.50 to $1.50
per acre-foot when the program
becomes operational rather than
experimental. Reported costs of
programs in California have generally
been within this range.
It should be recognized that these
costs have been estimated for
"successful" projects. The cost per
acre-foot is a function not only of
the procedure used but also of the
water yield from the project. Project
yield, in turn, is dependent on both
the meteorological and hydrological
characteristics of the particular
area being see'ded and the prior
availability of facilities for con-
trolling and storing the water
developed.
Success of increase in precipitation
also depends on the dryness or wet-
ness of the particular year. In
this regard the favorable chances
for cloud seeding are minimal during
the dry years when water is most
needed, resulting in somewhat
smaller Increases in runoff than
-85-
those expected during normal or wet
years. This means that while a
weather modification project would
be effective where normal and wet-
year increases could be stored
either in surface or underground
reservoirs for use in ensuing drier
years, the value of this increased
supply would be minimal compared to
an increase during drier years.
The yield of the Central Valley
Project, the State Water Project,
and major local projects cannot be
materially enhanced by increases
during the wet years, because sur-
plus water is already available in
those years . An augmentation of
water supplies would have the
greatest economic benefit during
the dry and average years .
There are many unresolved technical
and legal problems in weather modi-
fication. More experience is re-
quired to detennine which conditions
are favorable for seeding and the
best methods of seeding for given
conditions. Not much is yet known
about possible downwind effects of
cloud seeding. Indications so far
include possible decrease, no
effect, or increase in precipitation
downwind from seeding project areas.
Pertinent legal questions relate to
the responsibility of cloud seeding
operators for any downwind effects
and the effect of cloud seeding in
increasing floodflows. In Califor-
nia, seeding with silver iodide
seems to be most effective on the
colder storms; and operations are
carried out to enhance snowpack in
critical flood regions, thereby
reducing the direct flood hazard.
The Department of Water Resources is
participating with Fresno State
College Foundation in studies con-
cerning weather modification for
increase in precipitation In the
Sierra Nevada. The work, scheduled
for completion in 1973-7^, consists
of development of planning guide-
lines for evaluating potential water
yield estimates and costs of weather
modification in California.
It is anticipated that experience
gained from increasing experimental
and operational activity in weather
modification will lead to resolu-
tion of many problems, greater
physical control, and an Increase
in potential for future weather
modification activities. On the
more exotic side, decreasing an
overabundant water supply on the
windward side of some mountain
ranges and increasing that precipi-
tation on the water-deficient lee-
side may sometime be possible. In
a program sponsored under the Bureau
of Reclamation program, the State of
Washington is investigating this
possibility.
The day of much more extensive
efforts to change the weather or
climate by altering worldwide wind
circulation or by steering entire
storms from ocean areas onto nearby
lands in need of rain is, as yet,
only in the visionary stage. Many
problems must be solved before this
can be accomplished or even shown to
be desirable. The solution of prob-
lems will be based in large degree
on knowledge gained from research on
programs of current interest with
more modest objectives.
Watershed Management
Watershed management embraces a
broad spectrum of land treatment and
related measures to optimize overall
productivity, considering food,
forage, timber, wildlife, minerals.
recreation, and water. For purposes
of this bulletin, however, watershed
management will be discussed from
the standpoint of possible means of
modifying vegetation to improve run-
off characteristics, including
quantity, quality, and timing.
The physical potential for increas-
ing water yield production through
manipulation of the vegetative cover
has been demonstrated through experi-
mental research conducted by the
U. S. Forest Service, University of
California at Davis, and other
organizations . The Department of
Water Resources has cooperated in
this work and has contributed
funds on the order of $900,000 over
the past decade. The research ^has
generally concluded that runoff can
■86-
be increased w
by a reduction
use associated
native vegetat
shown that the
extended later
that the magni
and the change
difficult to p
Ithln certain areas
in consumptive water
with the growth of
ion. It has also
duration of flow is
into the summer, but
tude of the increase
in timing of flow is
redict .
The three categories of vegetative
manipulation which are applicable
to certain areas in California are :
selective timber cutting within the
snowfield portion of the commercial
timber zone; clearing of deeper-
rooted vegetation within the foot-
hill and brushlands regions and a
replanting to grasses ; and eradi-
cation of riparian phreatophytlc
(water-loving) vegetation which is
most prolific along the lower eleva-
tion reaches of California water
Within the commercial timber zone,
selective strip cutting of timber
at widths of about one tree-height
has been demonstrated as a means of
reducing snowpack evaporation and
Increasing runoff without hastening
snowmelt. The clearing of larger
blocks of forest appears to Increase
both runoff and rate of snowmelt.
For brushland areas where the annual
rainfall exceeds about 15 inches,
the clearing of deep-rooted plants
and conversion to grass can result
in an increased water yield on the
order of 2 to 3 Inches annually on
the treated areas. It is estimated
that up to 800,000 acres of brushland
in the Sacramento Basin may be suit-
able for such conversion. A 3-lnch
reduction of consumptive use could
provide an increase in total basin
runoff of perhaps 200,000 acre-feet
annually.
Eradication of streamslde and lake-
side vegetation can reflect a sal-
vage of water of up to 0.5 acre-feet
annually per acre eradicated.
Although the eradication of phreato-
phytes is important in localized
situations, the area of plant growth
is small and the amount of water
which may be salvaged is not of
great consequence In consideration
of California's total statewide water
needs. Also, this streamslde vege-
tation often has scenic value and
provides food and shelter for wild-
life. Extreme care must therefore
be exercised in determining those
areas where plants may be removed
without detrimental effect on the
environment .
While each of the foregoing measures
has merit in certain areas, there
would be many difficult problems with
respect to a large-scale vegetation
modification practice throughout the
State required to significantly
Increase California's usable water
supplies. Tl-iese problems include:
legal rights to alter native vege-
tation on private and public lands,
the compatibility of such modifica-
tion with scenic and ecological
values, and the rights to the water
supply which may be salvaged. More-
over, as a large portion of the lands
are under private ownership, any
modification of cultural practices
would have to be demonstrated to be
economically advantageous to the
individual owners.
From the present s
and in view of the
watershed manageme
volving modlflcati
vegetation do not
attractive option
significant water
to meet increasing
Un de rsea Aqueduct
tate of knowledge
limitations,
nt practices In-
on of native
appear to be an
for providing
supply quantities
statewide needs.
A concept for conveying water sup-
plies from California's North
Coastal rivers to Central and South
Coastal regions via an undersea
aqueduct has been proposed for study
over the past decade by private and
public water planners.
This Is not a new source of
water, but is discussed in this
chapter because it is a subject of
interest to those who are concerned
with water development alternatives.
The plan most commonly envisioned
would consist of a large offshore
pipeline, possibly on the order of
30 feet in diameter, anchored on the
-87-
continental shelf at a depth of
about 300 feet. The pipeline would
extend a total distance of some 700
miles from the mouth of the Klamath
or Eel Rivers to delivery points in
the Central and South Coastal areas.
Various materials have been sug-
gested for the aqueduct. These in-
clude heavy-duty plastic, flexible
rubber, fiber glass, concrete,
steel, and aluminum. Considerable
additional research and testing is
required to determine the engineer-
ing feasibility and to provide
reliable estimates of costs associ-
ated with the fabrication, place-
ment, and maintenance of a large-
diameter undersea pipeline.
Additional study is also required
to determine the effects of the
pipeline upon the marine
environment ,
An undersea aqueduct is principally
an alternative method of conveying
water supplies for the coastal
areas. Its utilization would re-
quire the development of dependable
water supplies by onshore facili-
ties in much the same manner as
required for an overland aqueduct
system. Because of the highly
variable runoff characteristics of
Northern California rivers, major
storage reservoirs would be needed
in conjunction with either an under-
sea or overland aqueduct system to
provide regulation of the water
supplies to the more uniform con-
veyance schedules required.
An undersea aqueduct would also
necessitate location of a diversion
structure near the mouth of the
river which provides the water
supply source. The diversion
structure would require facilities
for passage of fish over the struc-
ture and screening facilities to
protect fish from being carried into
the aqueduct.
In December 1969 the U. S. Bureau of
Reclamation published a report en-
titled "California Under Sea Aque-
duct Prereconnaissance Study". The
report outlined the considerable
additional research needs and rec-
ommended an initial six-year
reconnaissance study program. The
recommended program was adopted by
the Congress and funds were appro-
priated for the first-year studies
now in progress .
Geothermal Water Resources
The term geothermal literally means
earth heat, and it refers to the
natural heat that is generated
beneath the earth's surface. While
rock temperature generally Increases
slowly with depth, the rise (or
geothermal gradient) is markedly
steep in certain localities. These
regions are called geothermal
provinces.
Recently attention has focused on
the intriguing possibility of uti-
lizing geothermal heat to distill
fresh water from sea water or from
the saline ground waters that some-
time occur in geothermal regions.
Since the initial temperatures of
geothermal waters are much higher
than sea water, little or no heating
may be required for their distil-
lation. In this respect, geothermal
brines are preferable to ocean water
for conversion to fresh water.
The necessary conditions for a geo-
thermal distillation facility in-
clude a geothermal heat source, an
adequate supply of brine, and a
favorable market for fresh water and
such by-products as surplus energy
and residual minerals. A feasible
means for disposal of waste products
which will neither pollute the
environment nor endanger wildlife Is
also essential. Although more than
182 thermal springs have been found
throughout California to date, only
3 areas have attracted interest from
the standpoint of commercial produc-
tion of geothermal energy. These
are: The Geysers, near Cloverdale in
Sonoma County; Casa Diablo, north-
west of Bishop in Mono County; and
southern Imperial Valley. At The
Geysers, two steam powerplants with
a combined rated capacity of 82
megawatts are operated by the Pacific
Gas and Electric Company and an
increase to 4ll megawatts is contem-
plated within the next few years.
Advancing Technology — — Promises additional sources of water
Clair Engle Plant
Sea water conversion
Weather modification studies continue
Mexico's development ot same geothermal
province found in California
The Casa Diablo region has been
prospected and tested but does not
at this time appear worthy of
exploitation. Neither The Geysers
nor Casa Diablo Is endowed with
large quantities of brine from
which fresh water could be produced
by distillation. The southern part
of the Imperial Valley, on the other
hand, appears to possess the physi-
cal conditions required for a geo-
thermal distillation facility. It
is the only place known at present
in California where geothermal
energy and heated brines are avail-
able in abundance.
Serious attempts to develop a natu-
ral steam source in Imperial Valley
began with the drilling of an unsuc-
cessful steam well in 1927. Since
that date approximately 30 wells
have been completed which have
established Imperial Valley as a
major geothermal province. The
area considered likely for possible
desalination extends generally from
the southern end of the Salton Sea
to the Gulf of Mexico. It covers
an area of about 2 million acres.
Production of steam has commenced in
the Mexican sector of Imperial
Valley at the Cerro Prieto field
which lies about 15 miles south of
the border town of Mexican. Pres-
ent arrangements call for the in-
stallation of a 75-megawatt steam
electric powerplant at Cerro Prieto
which is expected to be ready for
service in 1971. The plant will be
operated solely for power produc-
tion. The brines produced during
the process will be conveyed through
an open ditch for disposal In the
Gulfcf California.
A preliminary evaluation of the geo-
thermal potential of the Imperial
Valley, California, has been covered
by Dr. Robert W. Rex of the Univer-
sity of California at Riverside in
two reports entitled "Investigation
of the Geothennal Potential of the
Lower Colorado River Basin, Phase I"
and "Investigation of Geothermal
Resources in the Imperial Valley and
Their Potential Value for Desalina-
tion of Water and Electricity Produc-
tion, June 1, 1970". Dr. Rex's
geologic, geophysical and geochem-
ical studies have established that
six and possibly as many as nine
geothermal hot spots exist in the
region lying between the Salton Sea
and the Mexican border and that 1 to
3 billion acre-feet of heated brine
may be stored In the sedimentary
formations between depths of 5,000
and 20,000 feet. Chemically these
waters appear to be no more saline
than many oil field brines. Their
temperatures range from 500 to 700
degrees Fahrenheit, as measured in
the formations at depth.
According to the University report,
brine reserves may be sufficient to
support 1,000 to 3,000 geothermal
wells at an average yield per well
of 1,200,000 pounds per hour of
steam. This is equivalent to 10.6
acre-feet of fresh water per day for
each well. The total projected
production rate for full operation
therefore would range between 3.6
and 10 million acre-feet per year.
At this rate, it would take from
100 to 850 years to exhaust the
available brines. A suggestion has
been made that the productive life
could be extended and possibly
doubled by recharging the geothermal
aquifers with sea water imported
from the Gulf of California.
If the geothermal water resource In
the Imperial Valley should prove to
be a practicable water supply, it
would be strategically located to be
of assistance in solution of the
water quantity and quality problems
relating to the Colorado River. It
could be a potential substitute for
Colorado River water diverted to the
Imperial and Coachella Valleys and
to the Coastal Plain of Southern
California, thus making those sup-
plies available for diversion to
other areas within California, and
to other states or Mexico. It might
also be used to dilute diversions
from the Lower Colorado River to
Improve their qualities. If electri-
cal energy from geothermal resources
could be produced at a favorable
cost, desalination of a portion of
the drainage waters from Imperial
and Coachella Valleys and their re-
use might be feasible. Conceivably
-90-
problems of the increasing salinity
of the Salton Sea might also be
solved, at least in part, by the use
of such waters.
Further investigation of the
Imperial Valley province is required
before the feasibility of a large-
scale geothermal operation can be
reasonably examined. In particular,
more knowledge is needed of geologic
factors (l) to permit refining the
estimates of available geothermal
heat and ground water brines, (2)
to explore procedures for recharging
brine aquifers and for the return
of saline residual fluids by relnjec-
tion into deep formations, and (3)
to develop more definitive cost
information.
Study of the region is continuing
by the University of California,
Imperial Irrigation District, U. S.
Bureau of Reclamation, and the
Department of Water Resources.
Nonstructural Alternatives
In planning to meet future water
resource needs, alternatives should
be considered that could result in
reduction or redirection of those
needs. These are referred to as
"nonstructural" as they do not
involve the physical construction
of projects; rather, they consist
of major changes in social, econcmic,
environmental, technological, and
governmental factors that may affect
water demand. Examples of such
alternatives are direct reallocations
of water supplies to more valuable
uses, reductions in water use and
waste water disposal through pricing
policies, technical improvements
that increase efficiency of water
use, improvements in water quality
management, land use policies
(including floodplain management),
and planned location of industries.
Reallocation of water supplies,
pricing policies, and Increased
technical efficiency in water use
are discussed in this section. Other
nonstructural alternatives concern-
ing environmental impacts on water
needs are discussed in Chapter VIII.
Reallocation of Water Supplies.
This would be a direct means of
bringing about the transfer of water
use from lower-return to higher-
return purposes, such as from irri-
gation to urban use. Reallocation
of water supplies from an agricul-
tural to an urban economy was, in
effect, accomplished by the City of
Los Angeles in the purchase of water
rights in the Owens Valley for ex-
port to Los Angeles via the Owens
River Aqueduct. The practicability
and advisability of such a course of
action in the future remains to be
seen and involves many considerations.
Possible economic and social disrup-
tion, both present and future, in
one area must be weighed against the
benefits accruing to another. Gradu-
al reallocation of water involving
relatively small reductions through
increased efficiency of water use
could minimize the problem. Serious,
practical difficulties remain, how-
ever. Perhaps the most notable
involves legal and institutional
constraints related to California's
complex water rights structure. Any
transfer of such rights could entail
lengthy negotiations or condemnation
procedures, involving, among other
things, appropriate compensation for
all interests directly or indirectly
affected by the transfer, such as
users of return flow, ground water,
etc .
Pricing Policies . Appropriate pric-
ing policies, combined with increased
marketability of water and/or water
rights, could ultimately accomplish
the same end as would a direct re-
allocation of water between uses.
Water use generally is influenced by
prices charged by retail water
agencies, such as irrigation districts
and city water departments. These
prices, in turn, are partially
affected by the pricing policies of
local wholesale agencies, and those
of the federal and state agencies.
The pricing policies of the latter
are determined by provisions of
reclamation law and by the provisions
of the State's contracts with the
wholesale agencies.
-91-
Local agencies can and do influence
the types and quantities of water
use through pricing policies which
can be adjusted to meet changing
situations. For example, water use
per capita can be reduced by shift-
ing from a flat rate (water charges
per month not affected by use) to
metering (water charges affected by
use). In metered systems, water
use per capita can be reduced by
shifting from a utility to an in-
verted utility rate structure, in
which the unit price of water
increases as the quantity of water
increases; or by increasing water
charges and decreasing taxes on
assessed valuation. Such shifts in
pricing policies may appear increas-
ingly attractive to local agencies
as the costs of new supplies in-
crease. The development of new
water pricing policies would require
detailed study of their social,
environmental and economic conse-
quences. The actual impact of a
price chang,e on the quantity of
water used would have to be deter-
mined more accurately before pricing
policies could be properly included
in the water planning process. Pre-
liminary studies by the Department
Indicate that for the urban South
Coastal area a 10 percent increase
in price would reduce per capita use
by 3 percent. The Impact upon cer-
tain industries and some agricul-
tural crops would be greater, how-
ever. In addition, any increase in
the price of water sufficient to
curtail water use would have to be
weighed against the possible impact
on Industrial expansions and employ-
ment or the possible Increase in
prices paid by consumers for the
products of the affected industries.
Consideration also must be given to
the impact upon lower income groups —
those who could least afford a price
increase. The economically dis-
advantaged may be forced to use less
water on lawns, shrubs and trees
causing a blighted local environment.
Increased Efficiency of Water Use,
frice increases can encourage
farmers to invest in more efficient
techniques of irrigation and encour-
age recycling in industry. Household
uses could be reduced by non-water-
using toilets, underground sprinkler
systems, etc. Efficiency of water
use can also be encouraged through
information, education, and social
and cultural pressures that increase
awareness of conservation. In par-
ticular, increased corporate social
responsibility for water quality
will encourage reuse of water to
avoid social costs associated with
waste discharges.
Mitigation of
Colorado River Salinity
This chapter has mentioned earlier
that the problem of increasing
salinity in the Colorado River may
eventually be solved, at least in
part, by the importation of good-
quality water from outside the
Colorado River Basin. However, it
is unlikely that this solution, if
found to be desirable, would be
available before 2000.
In the meantime, estimates in a
report of the Colorado River Board
of California, entitled "Need for
Controlling Salinity of the Colorado
River", August 1970, are that pro-
jected developments in the Upper and
Lower Divisions of the Colorado
River Basin will cause the salinity
of the River to increase. For
example, the report predicts that
salinity of the River at Imperial
Dam, the diversion point for the
Imperial and Coachella Valleys, will
increase from an average of 85O
parts per million between I963 and
1967, to an average of 1,3^0 parts per
million by 2000, if no preventative
measures are taken.
The report describes possible pro-
grams to control salinity of the
River. In addition to augmentation
with water supplies of low salinity,
it mentions removal of salts from
the River or its tributaries and
reduction of water losses by phreato-
phyte control and water salvage proj-
ects. It also lists a number of
sources of salinity in both the
Upper and Lower Divisions of the
Basin which it states could be con-
trolled by individual projects. The
-92-
report estimates that, with these
projects in operation by 2000, the
projected concentration of salinity
at Imperial Dam would be reduced
from 1,340 parts per million to
1,010 parts per million.
In addition to the projects des-
cribed in the report, there may be
other ways of preventing increases
in the River's salinity or of miti-
gating their effects in the various
service areas. The possible uses
of geothermal water resources and
desalination have been mentioned
earlier in this chapter. In the
South Coastal area, Colorado River
water could be diluted with water
of low salinity from the State
Water Project. Alternative ways of
utilizing water resources of the
Basin may also result in different
salt loads and different economic
returns to the respective areas.
A possible range of the magnitudes
of future salinity problems and all
reasonable alternative solutions
should be examined first on a
reconnaissance basis. Then a pro-
gram should be initiated to imple-
ment those solutions that are found
to be most desirable and are proven
to be economically sound through
feasibility studies.
Summary
This chapter has discussed the
array of possible future water sup-
ply sources and management measures
for augmenting California's depend-
able water supplies. It has pointed
out that to the present time water
demands have been met primarily
through traditional development
approaches involving the regulation
and conveyance of surface water
from natural sources and the extrac-
tion of underground supplies.
In addition to the discussion of
traditional approaches, information
has been summarized regarding the
potential for several other possible
measures which the Department of
Water Resources believes will become
more significant in the future and,
therefore, warrant serious further
study. These potential sources
include : greater reuse of present
water supplies through water recla-
mation practices: more effective
management of ground water resources
in coordination with surface sup-
plies; desalting of sea water and
brackish water; weather modification;
watershed management; and the poten-
tial which may exist for obtaining
usable water supplies at economi-
cally competitive costs from geo-
thermal sources.
Chapter V contains brief discussions
on the status of investigative
activity concerning a Western States
water program and on the research in
progress regarding the possible
future role of an undersea aqueduct.
It has also mentioned certain insti-
tutional measures concerning supply
reallocations, pricing policy modi-
fications, and increased efficiency
of use, which could be implemented
to stretch the existing supplies
and to discourage wasteful practices.
The Department of Water Resources
considers the various measures dis-
cussed in Chapter V to be comple-
mentary. Although many of them are
not presently considered to be
acceptable for either technological
or social reasons, additional re-
search and investigation may very
well indicate that each of the
options discussed will have a role
in the management of California's
water resources to meet future
demands .
-93-
Eel River North Coastal Are
Eureka Newspaper, Inc
Most ol the water is produced during the \i'inter stomts, frequently causing devastating tloods
DPW - Division o( Highv,
Regulation is needed to reduce Hood flows and make the water available during the sunmer months
CHAPTER VI. REGIONAL WATER DEMAND-
WATER SUPPLY RELATIONSHIPS
Chapter IV discussed statewide water
demands and summarized pertinent
water demand information by the 11
hydrologlc study areas. This chap-
ter discusses the derivation of
present and projected demands for
water to 199O and 2020 by Individual
hydrologlc study area, and the out-
look for satisfaction of those
demands from additional local sources
and other possible potential sources
described in Chapter V. It indi-
cates for the areas of water defi-
ciency the timing and magnitude of
need for additional water supplies
in excess of the local development
potential that may have to be made
available from other sources.
The water demand-water supply rela-
tionships for the individual study
areas are depicted graphically in
Figures I5 through 36. The loca-
tions, boundaries and designations
of the hydrologlc study areas are
shown on Figure 4.
North Coastal Area
The North Coastal area is by far
the most water-abundant area in
California, producing about 40 per-
cent of the State's total surface
water runoff. The area sustains
lumbering, recreation, and fishing
industries which are the mainstays
of the economy. Although only
13 percent of the area consists of
valley land, agriculture also is
important and accounts for the
primary applied consumptive water
demand. In I967 total agricultural
demand approximated 660,000 acre-
feet per year. More than 80 per-
cent of 1967 irrigated acreage was
located in the upper Klamath River
Basin (including Shasta and Scott
Valleys). The Klamath River Project
of the U. S. Bureau of Reclamation
provided about half of the upper
Klamath water supply and the remain-
der came from local stream diversion
and ground water. The remaining
irrigated agriculture is scattered
throughout the area and is served by
stream diversions and ground water
development .
Irrigated acreage is not expected to
expand greatly in the future
(30,000-acre increase by 2020)
because of the constraints of cli-
mate and marketing; however, chang-
ing crop patterns and increased use
of sprinklers will be significant
in raising the economic level of
agriculture. The greatest increase
in irrigation is expected to be in
the Scott-Shasta Valleys area.
In 1967 total urban water use in the
North Coastal area approximated
100,000 acre-feet per year. Of this,
about 70 percent or 70,000 acre-feet
was attributable to lumbering and
related wood products industries.
Although technological advances in
the industry are expected to stabi-
lize emplojTnent at about present
levels, output of the industry is
projected to increase with fuller
utilization of available raw
materials. As a result, the
lumbering and wood products indus-
tries will account for at least half
of the projected increase in the
area's total net water demands.
An increase In population and re-
lated domestic and other uses will
account for the remainder.
The present (1967) and projected
1990 and 2020 population, land use,
and water demands in the North
Coastal area are shown in Figure 15.
The North Coastal streams support
annual runs of 350,000 to 400,000
king salmon, 125,000 silver salmon
and perhaps a million steelhead. The
magnitude of these resources for
sport fishing and commercial catch
is comparable to those of the
Columbia River.
-95-
FIGURE 15
2020
1990
1967
2 3
100,000 PERSONS
POPULATION
n
IL
URBAN
F I IRRIGATED
■\
REMAINING IRRIGABLE
n.
5 6
_1 L
100,000 ACRES
LAND USE
AGRICULTURAL
URBAN
7^
8
100,000 ACRE -FEET
APPLIED WATER DEMANDS
1.2
LI
LO —
0.9 —
PROJECTED (MET WATER DEMANDS ^
^^,»»'*'^ Required Additional Supplies*
—
y^ ^_^^~--^ ^^^Cl_ NET WATER SUPPLIES EXISTING OR
X ^^^^--^"^ UNDER CONSTRUCTION IN 1,000 AF/YR. ~
1967 1990 2020
Local Surface Water Development 550 590 600
Groundwater 150 180 200
—
Klamath Project 250 250 250 —
Total Net Supplies 950 1020 1050
* Potential additional supply sources: Local area surface water developments including
Butler Valley Project.
1 1 1 1 t
1970
1980
1990
2000
2010
2020
YEAR
PROJECTED WATER SUPPLIES AND NET WATER DEMANDS
NORTH COASTAL HYDROLOGIC STUDY AREA
-96-
FIGURE 16
E: Bar Chart Units Are Million Acre-Feet Per Yeor
-97-
These streams make a major con-
tribution to the commercial salnon
catch in California and to a less-
er extent in Oregon and V/ashington.
Commerical salmon catch in 1967 at
Northern California ports totaled
5.3 million pounds with a value of
S2.8 million. I^rge volumes of
water are required not only for
transportation of adult and younr;
fish to complete their life cycle,
but also to "flush out" sediment
accumulations in spawning and
nursery areas, keep water auality
at a level compatible to fish, and
prevent the encroachment streamside
vegetation.
At the present time contracts
between local and federal agencies
and the Department of Fish and Game
are in effect on three North Coastal
rivers for releases aggregating
680,000 acre -feet per year to main-
tain salmon and steelhead population.
The North Coastal area is inter-
laced with a variety of scenic
flowing streams and rivers. Increas-
ing each year are the numbers of
sightseeing, rafting, canoeing and
swimming enthusiasts who place high
value on the environmental aspects
of flowing streams, proper forest
practices and clean air. Mainte-
nance of flowing streams for recre-
ational purposes is important and
the North Coastal area with appro-
priate water projects has an oppor-
tunity to preserve and improve
streams for these activities.
The expected future demands for
water in the North Coastal area is
small in comparison to the amount
of water available. However, most
of the water is produced during the
winter storms, frequently causing
devastating floods. Regulation is
needed to reduce the floodflows and
to make the water available during
the dry months when it is needed.
In summary, total net water demand
in the North Coastal area, exclud-
ing fish environmental needs, is
forecast to increase by about
200,000 acre -feet by 2020, one -half
of which will be for pulp and paper
industry. It is expected that
nearly 25 percent of the total in-
creased demand will be met from
extension of service from existing
developed surface sources, another
25 percent from additional ground
water extraction, and about half, or
100,000 acre-feet, will have to be
provided from new sources. Based on
the assumption that the future pulp
and paper plants would be located in
the Humboldt Bay area, water could
be provided by the authorized
Butler Valley Project on the lAad
River, with a water supply capability
of 160,000 acre-feet per year.
North Coastal water supply-demand
relationships are depicted graphi-
cally in Figure 15; and the area's
location and a geographical compari-
son of water supplies and demands
are shown in Figure I6.
San Francisco
Bay Are'a
When considered as a whole the
San Francisco Bay area has suffi-
cient water supplies to meet its
needs until sometime after 2000.
Like so many other areas of the
State, however, such broad treat-
ment neglects localized conditions
which may indicate water defi-
ciencies in certain areas at a much
earlier date. The Bay area has a
complex system of water supply and
can logically be treated in two
parts — the area north of and the
area south of San Francisco Bay. In
the ensuing discussion these parts
will be referred to as the North
Bay area and the South Bay area.
The North Bay area is both agri-
cultural and urban in character,
with irrigated agriculture account-
ing for about 60 percent of the
total present water demands. How-
ever, the area is experiencing rapid
urbanization which is expected to
continue, particularly in Marin and
southern Sonoma Counties. While
Irrigated agriculture is expected
to show some increase, urban de-
mands are anticipated to account for
about 70 percent of the total wat--
demand by 2020.
-98-
At present, water needs in the North
Bay area are being met from ground
water, several local projects, two
important federal projects (Lake
Mendocino on the East Fork of the
Russian River in Mendocino County
and Lake Berryessa, a feature of the
Solano Project, on Putah Creek in
Napa County) and the North Bay
Aqueduct of the State Water Project.
Not to be overlooked is the aque-
duct system serving Sonoma and
Marin Counties, constructed by local
water agencies.
Some areas in Napa and Sonoma
Counties, however, are currently in
a state of ground water overdraft
which will continue unless addi-
tional facilities are built to meet
the projected increase in water
demands. In fact the North Bay
area \')ill have an aggregate annual
supplemental demand for water of
about 50,000 acre-feet within the
next 20 years, increasing to
approximately 350,000 acre-feet by
2020. This increase will result
primarily from expansion of urban
development .
An analysis of proposed projects
indicates that most of the addi-
tional water needs can be met by
further development of local sup-
plies. The Russian River and its
tributaries offer the greatest
potential, although additional sup-
plies will be necessary from
various other local projects and the
North Bay Aqueduct.
The South Bay area ranks second
only to the South Coastal area in
urban growth. It is highly urban-
ized at the present time and is
expected to become mare so in the
future. Population is forecast to
more than double between 1970 and
2020. Irrigated agriculture, with
a net demand of 166,000 acre-feet
at present (1967) is expected to be
virtually eliminated by urban
encroachiment by 2020.
The generally excellent water supply
situation in the South Bay area is
due largely to the forward-looking
planning and development of both
local and importation systems by
the major local agencies. Local
surface and ground water supplies
have been almost fully developed
and the area depends heavily upon
four major import projects: the
Hetch Hetchy Water System of the
City of San Francisco; the Mokelumne
Aqueduct of East Bay Municipal
Utility District; the Contra Costa
Canal of the Central Valley Project;
and the South Bay Aqueduct of the
State Water Project .
The total amount of water delivered
in 1967 by the four systems was
nearly 500,000 acre-feet. Planned
expansions would bring the total
import capacity of these systems to
an estimated 1,150,000 acre-feet
per year. In addition a new pending
contract between the East Bay
Municipal Utility District and the
U. S. Bureau of Reclamation will
provide for 150,000 acre-feet of
water annually in 2020. This addi-
tional water has been included in
the Central Valley Project water
supply for the areas as shown in
Figure 17.
In addition, provision must be made
to correct a serious ground water
overdraft situation in Santa Clara
Valley which has contributed to
salt water intrusion near the Bay.
Possible solutions include advanc-
ing planned delivery schedules of
water from the South Bay Aqueduct,
and the federal San Felipe Division
of the Central Valley Project.
Waste water reclamation may become
a more important factor in balancing
the area's water supplies and needs.
A small allowance has been made for
this possibility. Desalting may
also provide a water supply at such
future time as costs become
competitive .
The principal sources of impairment
to the quality of water in the
San Francisco Bay area include
domestic and industrial wastes,
irrigation return water, and saline
water intrusion into ground water
aquifers. Saline water has
seriously degraded once usable
ground water supplies in basins
adjacent to the Bay. This condition
has been caused by prolonged periods
-99-
FIGURE 17
2020
1990
1967
URBAN
IRRIGATED
REMAINING
IRRIGABLE
^AGRICULTURAL
^
URBAN
1
— . 1_
2
1
3
— L_
1.000.000 ACRE- FEET
APPLIED WATER DEMANDS
1970
1980
2010
1990 2000
YEAR
PROJECTED WATER SUPPLIES AND NET WATER DEMANDS
SAN FRANCISCO BAY HYDR0L06IC STUDY AREA
2020
-100-
FIGURE 18
SAN FRANCISCO BAY
HYDROLDGIC STUDY AREA
NET WATER SUPPLY
NET WATER DEMAND
I I SUPPLEMENTAL WATER DEMAND
N NOTE: Bar Chort Units Are Million Acre-Feet Per Year
■101-
of overdraft and progressive lower-
ing of the water table below sea
level. Continued urban growth Is
Intensifying the problems of domes-
tic and Industrial waste disposal.
The recently completed study by the
State Water Resources Control Board
of water quality of the
San Francisco Bay-Delta estuary
showed that toxicants and biologi-
cal growth stimulants from indus-
trial, municipal and agricultural
waste waters pose the largest water
quality control problem for those
waters. With a continuation of
existing methods of disposal, the
present waste water inflows of
600,000 acre-feet a year would
increase to 2,100,000 acre-feet by
2020 at the projected level of
urban development. The biochemical
oxygen demand (BOD) and nitrogen
loads generated (before treatment)
would Increase about fourfold.
To reduce the potentially adverse
effects of these increased waste
discharges the study proposed a
regional system for waste water
collection and disposal that would,
by 2020, reduce Inland discharges
in favor of ocean outfalls located
off San Mateo and/or Marin Counties.
An additional recommendation covered
reclamation plants at Inland sites
where waste water from residential
areas could be diverted and reno-
vated for uses such as Delta out-
flow, ground water recharge, and
Irrigation.
The State Water Resources Control
Board Is following up the Bay-Delta
study by sponsoring and financing
an l8-month supplementary investi-
gation by the Departments of Water
Resources and Fish and Game that
will cover sources, effects, and
control of toxicity and growth
stimulants in Bay-Delta waters. The
studies conducted so far have indi-
cated that area-wide planning for
water quality management using a
systems approach Is necessary, as
change in water quantity or quality
within any portion of the Bay-Delta
system can have an Impact on the
entire environment. Progressive
damage to the aquatic environment
will result unless an adequate
system of facilities for treatment
and disposal of these waste waters
is developed, or other preventive
action is taken.
Demands for recreation in the
San Francisco Bay area, the S::ate's
second largest population center,
are not being met and will probably
not be met in the foreseeable
future due to the lack of facilities
caused by lack of funds, increasing
population, decreased work-week
time and increased spending power
per capita. An attempt to keep up
with these demands will be made,
and many new facilities will be
developed utilizing available urban
and natural park settings, the
available shoreline and man-made
features. The State estimates that
outdoor recreation demand In this
area will approximately double In
1980 over i960 levels. The Califor-
nia Outdoor Recreation Plan (i960)
indicates 60 percent of all recre-
ation is oriented around water-
associated areas, and that the
majority of recreation needs are
within 1 hour travel time from
urban areas. The San Francisco Bay
area has the physical attributes
for meeting these recreation needs,
and the area can expect heavy
future recreation use.
Major fish and wildlife resources
exist in the San Francisco Bay area.
An Important segment of the State's
8 million striped bass inhabits
San Francisco, San Pablo, and
Suisun Bays. It is an important
flyway for waterfowl, in addition
to having a sizable deer population.
Approximately 80,000 steelhead and
salmon spawn in the area, 50,000 in
the Russian River drainage alone.
The preservation and, where possible,
enhancement of recreational, fish
and wildlife resources of the
San Francisco Bay area are major
considerations in planning for the
area's water needs. Of particular
importance are the compensatory
measures required when dams and
reservoirs are constructed on anad-
romous fish streams and the provi-
sion for replacing wildlife habitat
-102-
due to project development or other
competing; land uses. In this re-
gard, streamflow releases aggregat-
ing some 120,000 acre-feet are made
under agreement between project-
operating agencies and the Depart-
ment of Fish and Game. Moreover,
Joint studies are currently under
way by the Departments of Fish and
Game and Water Resources to define
the amount and quality of water
required to maintain the Suisun
Marsh under future salinity con-
ditions .
The consumptive use of water by
recreationists at outdoor camping
and picnic facilities is not large.
However, the water needs of the
hundreds of thousands of annual
visitors to the Bay area is sub-
stantial and have been included as
part of the urban water demand.
In summary, the total net water
demands in the San Francisco Bay
area are projected to include from
1,150,000 acre-feet per year at
present (1967) to an estimated
2,740,000 acre -feet in 2020.
Prospects in general appear to be
good for satisfying water demands
in the San Francisco Bay area until
about 2000 through local projects,
ground water supplies, and existing
local, state, and federal import
systems. Although the total South
Bay area overall water supply
appears adequate beyond 1990,
individual communities and service
areas may have problems either as to
supplies or in distribution system
capacity and reliability. One
example is the Contra Costa County
Water District where new or enlarged
conveyance and storage works will be
needed in the mid-1970s to enable
the District to meet peak water
demands and to give protection
against interruption of the water
supply. The District is actively
promoting the modified Kellogg
Project as the solution to their
Immediate water supply problem.
Water demands and existing and
potential supplies are equated
graphically in Figure 17. A geo-
graphical comparison of water
supplies and demands within the area
is shown on Figure I8.
Central Coastal Area
The Central Coastal area essentially
spans the coastal interval between
the metropolitan centers of the
San Francisco Bay and the South
Coastal area. Mountain ranges that
follow the coast extend through the
area with many fertile valleys
between them. The major drainage
basins are the Pajaro, Salinas,
Santa Maria, and Santa Ynez Rivers
and their tributaries.
The economy is based primarily on
agriculture and related activities;
but the extraction and refining of
petroleum, mining, commercial fish-
ing and lumbering are also important.
A number of military establishments
also contribute significantly to the
economy of the area.
In 1967 about 25 percent of the
truck crops produced in California
were grown in the intensely devel-
oped valleys of the area. That yeai)
about 800,000 acre-feet of water
from local ground and surface water
supplies were used to irrigate
approximately 350,000 acres. Irri-
gated acreage is not expected to
expand greatly in the future
(390,000 acres by 2020) because of
scattered parcels that would be
difficult to farm economically,
considering water costs.
The major urban centers of the
Central Coastal area are situated
in the Monterey Bay urban complex
and the cities of San Luis Obispo,
Santa Maria and Santa Barbara.
Present urban net water demands
amount to about 150,000 acre-feet
per year. A rapidly increasing
population is expected to increase
these demands to 470,000 acre-feet
by 2020. Also, the present water
requirement of 5,000 acre-feet per
year for fish, wildlife and recre-
ation is expected to double by 2020.
The present (I967) and projected
1990 and 2020 population, land use
and water demands in the Central
-103-
FIGURE 19
2020
1990
1967
1
1
1
(M-
■
URBAN
~I IRRIGATED
REMAINING/
IRRIGABLE
IL
? 1 9 ? '9 '^
AGRICULTURAL
/
URBAN
/
1
1 1
2
i
1,000,000 PERSONS
POPULATION
100,000 ACRES
LAND USE
1,000,000 ACRE- FEET
APPLIED WATER DEMANDS
.4 —
.0 —
0.8
PROJECTED NET WATER ^.^-^'"'^
--
^
—
DEMANDS — — ^...^^^^^ ^.^'^^
—
^^^''^ Required Additional Suppl
es:
^^^"^ potential additional supply sources: loc
Jl surfac
e
^„,^''^ development, desalination, additional CVP-SWP
imports
, ground
^ _____^ -^^NET WATER SUPPLIES
^^_^ — EXISTING OR UNDER CONSTRUCTION "
^e:^ — IN 1,000 AF/YR.
1967
1990
2020
Local Surface Development 40
50
50
Ground Water: Safe Yield 730
750
750
Ground Water: Overdraft 120
15
15
—
Central Valley Project 0
80
110 —
Other Federal: Twitchell, Salinas, Cachuma 50
55
55
State Water Project 0
Total Net Supplies 940
1 1 1 1
80
1030
80
1060
1970
1980
1990
2000
2010
2020
YEAR
PROJECTED WATER SUPPLIES AND NET WATER DEMANDS
CENTRAL COASTAL HYDROLOGIC STUDY AREA
-104.
FIGURE 20
CENTRAL COASTAL
HYDROLOGIC STUDY AREA
I 1 NET WATER SUPPLY
Egjl NET WATER DEMAND
I 1 SUPPLEMENTAL WATER DEMAND
NOTE: Bar Chart Units Are Million Acre-Feef Per Year
SCALE OF MILES
0 8 16 24
-105-
Coastal area are shown in Figure 19.
Water demand and supply relation-
ships are also depicted on Figure
19 and the geographical distribution
in Figure 20.
Ground water is the main source of
supply in the Central Coastal area.
However, agricultural growth and
urban expansion has caused water
levels to fall in many areas such
as the Salinas Valley. A complex
of dams, canals and percolating
basins has been constructed to con-
serve runoff from the principal
streams and to place the water in
underground basins. San Antonio,
Nacimiento and Twitchell Reservoirs —
three of the largest in the area--
conserve more than 100,000 acre -feet
annually for ground water replenish-
ment, but water levels continue to
decline in some areas.
The present annual net water demand
of 940,000 acre-feet exceeds the
firm water supply by 120,000 acre-
feet as shown In Figure 19. The
difference is obtained from extrac-
tion of ground water in storage
(overdraft). The future ground
water overdraft shown is primarily
in Cuyama Valley in inland Santa
Barbara County, where no reasonable
alternative supply exists. Studies
indicate that there are large
volumes of water in some ground
water basins of the Central Coastal
area; and, it is likely that well
owners will continue to pump in
excess of the safe yield of certain
basins. Pumping will probably con-
tinue until limited by economics,
quality problems, legal restrictions,
or organizational controls.
Central Coastal Area lettuce bowl produces one-half ol California's and one-third of Nation's lettuce
-106-
Local water districts in San Luis
Obispo and Santa Barbara Counties
have executed contracts with the
State for delivery of more than
80,000 acre-feet annually from the
State Water Project by 1990. Also
the authorized San Felipe Division
of the Central Valley Project is
scheduled for annual deliveries of
80,000 acre -feet by I99O and
110,000 acre-feet by 2020. When
these projects are in full operation
the Central Coastal area will still
be deficient by about 130,000 acre-
feet In 1990 and 360,000 acre-feet
by 2020.
Almost all of the 1990 estimated
demand for supplemental water is in
the northern portion of the Central
Coastal area, mostly in the lower
Salinas Valley and to a lesser
extent in Santa Cruz County and the
coastal Monterey Coast-Carmel
Valley vicinity.
About half of the projected 360,000
acre-feet annual deficit In 2020 is
estimated to occur in the lower
Salinas Valley. The balance Is
forecast to be about equally divided
between Santa Cruz County, Monterey
Coast-Carmel region, and Santa
Barbara and San Luis Obispo Counties.
Importation of water from the San
Felipe Project is expected to pro-
vide for the foreseeable demands of
the South Santa Clara and Holllster
areas .
The question of identifying the
sources of water which could most
beneficially meet these deficien-
cies should be considered in terms
of the relative economics of alter-
native water supply possibilities
physically available to satisfy the
specific deficiencies within the
area. They Include the options of
additional local surface and ground
water development, although this
potential Is small in Santa Barbara
County; and the possibilities of addi-
tional Imported water supplies, and
desalting for urban purposes. In
addition, the reuse of reclaimed
urban waste water should be seri-
ously considered for ground water
recharge and/or Irrigation use.
South Coastal Area
The South Coastal area is the most
populous and the leading Industrial
and commercial center In the State.
It is one of the fastest growing
areas in the entire Country, and
this growth is likely to continue.
There has been a shift from an
almost entirely agriculturally
based economy to one of industry
and commerce. The resultant econom-
ic diversification and prosperity
can be attributed to the discovery
of oil and the development of the
petroleum Industries and its
favorable climatic conditions, which
attracted the aircraft and national
defense-oriented industries.
Reflecting the increasing urbaniza-
tion, the total water demands of
the South Coastal area, including
agricultural demand, are projected
to grow from about 2.5 million acre-
feet per year at present to 5.3
million acre-feet in 2020, more
than twice the present demand.
To meet present water demands, the
South Coastal area presently
depends on: (l) local surface and
ground water supplies, which are
almost fully developed if the use
of water is based on the average
annual natural replenishment;
(2) the Los Angeles Aqueduct, which
was enlarged in 1970 to deliver
approximately 480,000 acre-feet
annually to the City of Los Angeles;
and (3) the Colorado River Aqueduct,
now delivering water at almost full
capacity of about I.I8 million acre-
feet per year to the Metropolitan
Water District of Southern Califor-
nia. Currently, the total water
supply available to the area Is
approximately equal to Its water
demand (2.5 million acre-feet in
1967).
Potential future local surface
water supply projects in the South
Coastal area are limited, and water
available from them will not offer
a long-term solution to the area's
needs. Fallbrook and DeLuz Reser-
voirs on the Santa Margarita River,
as well as additional surface water
-107-
FIGURE 21
2020
1990
1967
URBAN
IRRIGATED
REMAINING
RRI6ABLE
^AGRICULTURAL
/
URBAN
1 2 3
1 r 1
4
1
5
1
S
1. .
1,000,000 PERSONS
POPULATION
1,000,000 ACRES
LAND USE
1,000,000 ACRE-FEET
APPLIED WATER DEMANDS
2 —
PROJECTED NET WATER DEMANDS
^ Required Additional Supplies: Potential additional supply sources — desalii
further waste water reclamation, additional SWP imports, ground water withdr
storage.
NET WATER SUPPLIES
EXISTING OR UNDER CON -
ST RUCTION IN ipOO AF/YR.
1970
^^ Local Surface Wate
r Dev.
170
180
180
Ground Water: Safe Yie
Id
900
950
950
Ground Water Overdraft
0
0
0
Los Angeles Aqueduct
330
480
480
State Water Project
0
2200
2200
Colorado River Aqueduct
1060
520
520
Waste Water Reclamation
30
300
300
Total Net Supplies
2490
4630
4630
* May increase
to 600,000 acre
feet
per
vear
1980
1990
2000
2010
2020
YEAR
PROJECTED WATER SUPPLIES AND NET WATER DEMANDS
SOUTH COASTAL HYDROLOGIC STUDf AREA
-108-
FIGURE 22
SOUTH COASTAL
HYDROLOGIC STUDY AREA
I 1 NET WATER SUPPLY
I 1 NET WATER DEMAND
I 1 SUPPLEMENTAL WATER DEMAND
NOTE: Bar Chart Units Are Million Acre-Feet Per Yeor
-109-
development in the San Dieguito
River watershed in San Diego County,
are currently being studied. Proj-
ects were proposed for Sespe Creek
in Ventura County, but their near
future construction is not considered
likely.
In 1971 deliveries will begin from
the State Water Project to the
service areas of the Metropolitan
Water District of Southern CfeLLifornia
and other water agencies in the
South Coastal area. The total max-
imum entitlement to Project water
amounts to 2,204,000 acre-feet per
year .
The water supply from the Colorado
River will be reduced to about
550jOOO acre-feet per year when
the Central Arizona Project becomes
operational. It is expected that
this reduction will occur in the
mid-1980s. Nevertheless, the total
supply available to the South
Coastal area, including the full
State Water Project entitlements,
should be adequate to meet water
demands until beyond 2000, when a
demand for supplemental water is
anticipated to begin. Delivery of
full State Water Project entitle-
ments will require additional con-
servation developments, as the
presently developed firm Project
water supply is somewhat less than
the contract entitlements. The
water supply capabilities of the
State Water Project will be dis-
cussed in Chapter VII.
A substantial amount of water may
be made available from waste water
reclamation. By 2020, reclamation
of about 600,000 acre-feet annually
is believed feasible, even though
definite plans have been made only
for 300,000 acre-feet. However,
additional information and experi-
ence must be gained before the full
potential can be realized as a
long-term source of water supply.
For example, more definitive knowl-
edge must be gained regarding the
adequacy of underground recharge
capacity to accept (percolate)
large amounts of reclaimed water on
a continuous basis. Also, further
evaluation must be made concerning
the physical and economic require-
ments to maintain adequate quality
of the replenishing and receiving
waters to meet water quality cri-
teria specified by the Regional
Water Quality Control Boards.
Converted sea water probably will
satisfy a portion of the demand for
supplemental water in the South
Coastal area. While current costs
preclude its consideration as a
major source for the near future,
it may well become economical on a
large scale as technology in de-
salting processes continues to
develop and costs are reduced.
The quality of ground water, a
significant source of water to the
South Coastal area, ranges from
excellent to extremely poor. The
quality of water from San Gabriel
Valley, Upper Santa Ana River water-
shed, and San Fernando Valley is
generally excellent and the concen-
tration of dissolved minerals is
generally below 400 parts per million
(ppm), reflecting the quality of the
runoff from mountain ranges. The
quality of ground water in the
Coastal Plain of Los Angeles County
and the Coastal Plain of Orange
County reflects substantial influence
of man and the mineral concentration
reaches about 5OO ppm. Some iso-
lated areas, however, have concen-
trations exceeding 1,000 ppm,
reflecting the quality degradation
from sea water intrusion. The
quality of ground water in much of
San Diego County is generally poor--
700 to 1,U00 ppm. Ground water in
portions of Ventura County has poor
quality--above 700 ppm.
The quality of water imported to
the South Coastal area varies with
the source. Water from Mono-Owens
Valley has a dissolved mineral con-
centration of about 250 ppm.
Colorado River water at Parker Dam,
above which the Colorado River
Aqueduct originates, has a concen-
tration of about 750 ppm. A recent
report by the Colorado River Board
of California ("Need for Controlling
Salinity of the Colorado River",
published by the Colorado River
Board of California, August 1970)
-110-
presents estimates that st^linity of
Colorado River water at Parker Dam
will increase to 860 ppm by I98O
and 1,110 ppm by 2000, in the
absence of salinity control mea-
sures. If certain salinity control
projects identified in the report
are implemented and if they reduce
salt loadings as estimated, the
respective salinity values would be
820 and 830 ppm. Without such
projects or other measures, costs
of treatment would be increased
substantially and usefulness of the
water for some purposes would be
impaired. To the extent such water
could be diluted with water from
the State Water Project, its adverse
effects could be eliminated or re-
duced. Water to be delivered by
the State Water Project will re-
flect the quality objective of
220 ppm, which is incorporated in
the water supply contracts.
The water demand-supply relation-
ships in the South Coastal area
are depicted graphically in
Figure 21, and the geographical
locations of water demands and
available supplies are shown in
Figure 22.
It can be seen from an inspection
of Figure 21 that the assumed level
of reuse of reclaimed water has a
considerable effect on the timing
of need for supplemental water.
The line on that figure depicting
available supplies is based on the
definitely planned reclamation of
waste water in the amount of
300,000 acre-feet per year. If
this value were increased to
600,000 acre-feet per year, as
future experience may well prove
to be the case, the effect would
be to delay the need for supple-
mental water.
In addition to the further use of
reclaimed water, the total demand
for supplemental water in the
South Coastal area in 2020 could
be met from several alternative
sources: surplus deliveries of
Project water during the earlier
years, to be stored underground for
later use; water from supplementary
facilities to State Water Project;
converted sea water; and possible
interim use of ground water in
storage. It is probable that a
combination of some or all of
these alternatives will be employed
to meet the area's water demands.
Sacramento Basin
The Sacramento Basin is the second
largest water-producing area in the
State. On the average, about 21 mil-
lion acre-feet of natural runoff
annually originates in the basin,
amounting to about 30 percent of
California's total natural runoff.
The Sacramento River is the largest
stream in the State. It provides
for year-round navigation for
shallow-draft craft upstream as far
as Colusa. This is made possible
by releases from Shasta Reservoir,
the largest regulatory reservoir in
the Basin.
Like the North Coastal area, the
Sacramento Basin is subject to
periodic devastating floods. An
extensive system of flood control
works has been constructed over the
years by various agencies including
the U. S. Army Corps of Engineers
and reclamation and flood control
districts. The system includes
hundreds of miles of levees along
the Sacramento River and tributaries
and Shasta and Folsom Dams. The
recently completed Oroville Dam on
the Feather River and New Bullards
Bar Dam on the Yuba River are sub-
stantial additions to the flood
control system.
In all, the flood control works
within the Sacramento Basin have
functioned well in recent years to
minimize the disastrous flooding
which has been part of the history
of the Basin. Damages during the
extended periods of high runoff in
1969 and 1970 were light in compar-
ison with damages which would have
occurred without satisfactory
operation of the system.
Completion of Auburn Dam, now under
construction and construction of
the authorized Marysville Dam will
significantly increase protection
•111-
from major flooding in some of the
more urban areas of the Sacramento
Basin. The Corps of Engineers has
recently proposed construction of
two reservoirs on Cottonwood Creek,
a major west side tributary of the
Sacramento River near Redding.
Other possible projects are under
study on a number of streams. In
addition, proposals for channel
improvements and levees are under
consideration. Floodplain manage-
ment programs are also being ini-
tiated by local interests.
More than 90 percent of the water
used today in the Sacramento Basin
is for farming. Agricultural
water use is expected to increase
moderately in the future with an
annual applied water demand in 2020
of about 7.5 million acre-feet,
an increase of approximately 20 per-
cent over present (I967) levels.
Agricultural demands are expected
to rise at a more rapid rate prior
to I99O; after that date the in-
crease is expected to slow, partly
because of urban encroachment and
partly because most of the best
land with convenient water supplies
will be under irrigation by 1990-
Urban demands are expected to
approximately double by 2020. Most
of the urban growth is expected to
continue near present cities. In-
cluded in the future urban demand
is an allotment of about 60,000 acre-
feet for the paper and wood products
industry in the northern Sacramento
Valley.
The Sacramento Basin accounts for a
substantial portion of the statewide
fish, wildlife, and recreation water
requirements. This is due primarily
to several existing wildlife refuges.
Sacramento Valley
the area is well suited to rice culture.
-112-
In addition, many private organi-
zations flood farmlands in the fall
to provide waterfowl hunting
opportunities .
The present (I967) and projected
1990 and 2020 population, land use,
water demand, and usable water
supplies in the Sacramento Basin
are shown in Figure 23. The
geographic distribution of water
supplies and demands is shown on
Figure 24,
Total basin-wide developed water
supplies exceed total foreseeable
water demands in the Sacramento
Basin. Some water agencies in
favorable locations have more de-
veloped water available than the
indicated demand in 2020, partic-
ularly in the southeastern portion
of the Basin. Other areas do not
have sufficient supplies to fully
meet expected future needs.
Areas of indicated water shortages
are (1) the west side of the
Sacramento Valley, mainly in Yolo
and Solano Counties; (2) the Pit
River Basin, mainly in Big Valley;
and (3) scattered foothill and
mountain areas both on the east
side and west side, including Lake
County. Future supplemental de-
mands in Yolo and Solano Counties
can be met by the Indian Valley
Reservoir on Cache Creek to be con-
structed by the Yolo County Flood
Control and Water Conservation
District, and the West Sacramento
Canals Unit of the Central Valley
Project. The proposed Allen Camp
Unit would meet the projected
deficits in the Pit River Basin
and would make possible development
of a new wildlife refuge in Big
Valley. The authorized Lakeport
Project by the U. S. Army Corps of
Engineers could take care of a
significant part of Lake County
needs, while the proposed Middletown
Reservoir in the upper Putah Creek
drainage (part of the proposed West
Sacramento Canals Unit) would permit
agricultural development in that
portion of Lake County. Other
possibilities are the proposed
English Ridge import from the Eel
River and additional Cache Creek
storage .
Other areas of water shortage are
projected to occur in scattered
mountain and foothill areas on the
western slopes of the Sierra Nevada-
Cascade Range, as a result of the
influx of people taking advantage of
the pleasant environment.
There is a substantial amount of
additional land suitable for many
irrigated crops in the Sacramento
Basin. Water costs for new develop-
ment generally will be less than in
other areas of the State. Climatic
conditions for agriculture are almost
as favorable as in the San Joaquin
and Tulare Basins; therefore, a
shift in new land development to
the north is possible with corre-
sponding effects on the projections
shown here.
Because of its high water require-
ment, the future of rice acreage is
an important factor in projecting
future water demands in the Sacramento
Valley. With many acres of fine-
textured clay soils, inexpensive
water and high yield potential, the
area is well-suited to rice culture.
Projection of future rice acreage is
particularly uncertain, as it is
subject to governmental controls
and foreign markets. Reported rice
plantings in 1967 in the Sacramento
Valley were about 320,000 acres;
rice acreages for the 1990 to 2020
period were assumed in this bulletin
to remain essentially constant,
approximating the 1967 level.
Preservation of the present high
quality of water in the Sacramento
River is of paramount importance.
It concerns local water uses, fish
and wildlife, and uses dependent
upon water exported from the river
by the Central Valley and State Water
Projects. Quality of the river has
been under surveillance and inves-
tigation for a number of years.
In January 1969, the California
Regional Water Quality Control Board,
Central Valley Region, proposed
water quality control policy for the
-113-
FIGURE 23
2020
1990
1967
2
~~] URBAN
n.
IRRIGATED
REMAINING
IRRIGABLE
/
1
AGRICULTURAL
.
urban'
2 4 6
1 1 1
8
1
10
1
1,000,000 PERSONS
POPULATION
1,000,000 acres
LAND USE
1,000,000 acre -feet
APPLIED WATER DEMANDS
7.0 —
6.5 -
6.0 —
5.5 -
^
^
* Potential additional supply sources: ^^^^^^
West Sacramento Canal Unit, CVP; Allen Camp Unit, ^^^^"'^
CVP; Indian Valley Reservoir; Lakeport Project; ^^^^ Required Additic
nal Su
pphORj^
English Ridge Reservoir. ^^-''^
,^^
'"^^
projected net WATER DEMANDS -p^'"'^^ ^^^^"""'^
y^ ^-"""^^ NET WATER SUPPLIES
y^ ^/^ EXISTING OR UNDER CQNSTRUC-
y^ ^^ TION IN 1,000 AF/YR
>r y^^ 1967
1990
2020
y y^ Local Surface Water Dev. 1960
2210
2380 —
y y^ Ground Water: Safe Yield 1010
1100
1180
^ y^ Ground Water: Overdraft 140
0
0
/^ y^ Echo Lake, Little Truckee Diversions 10
10
10
/ y^ Central Valley Project, including
/ / Sacramento River and American River
' y water rights 2210
2750
3080
/ Other Federal 170
170
170
State Water Project 0
40
40
Total Net Supplies 5500
1 1 1 1 1
6 280
6860
1970
1980
1990
YEAR
2000
2010
2020
PROJECTED WATER SUPPLIES AND NET WATER DEMANDS
SACRAMENTO BASIN HYDROLOGIC STUDY AREA
■114-
FIGURE 24
SACRAMENTO BASIN
HYDROLOGIC STUDY AREA
I 1 NET WATER SUPPLY
I 1 NET WATER DEMAND y
I 1 SUPPLEMENTAL WATER DEMAND -^
NOTE: Bor Chart Units Are Million Acre-Feet Per Year
1.0
0.5
0
1967 1990 2020
lis SOUTHEAST
I -2.0 1 1 1
,^^-of— l^J
: f CENTRAL BASIN
J ''n — rzn/ /
r '5
1.0
05
0
KEY TO STUDY AREAS
1967 1990 ^020 i^'J
1967 ,1990 2020
1 ^'
/
SOUTHWEST
ffl
1967 1990 2020
\
\
SCALE OF MILES
0 8 16 24
-115-
Sacramento River to apply from
Sacramento to Keswick Dam. Local
interests became concerned about
the possible consequences of the
proposed policy with respect to
future irrigated agriculture, and
in May I969 requested the Department
to assist them in a one-year study
of the impact of anticipated future
expansion of irrigated agriculture
on the quality of water in the
river.
Preliminary results of the study
showed that, although the 1990 an-
nual average mineral concentration
(as measured by electical conduc-
tivity) would be higher (30 to 58
percent at Preeport) than historic
values, the overall mineral quality
would not approach the historic
monthly extremes. No serious qual-
ity problems with respect to total
dissolved mineral concentrations
were indicated for the hydrologic
conditions studied.
A similar cooperative study was
initiated in January I97O for the
Feather River. Continuing water
quality studies of the Sacramento
Basin are necessary to keep abreast
with changes in water development
and project operations, as well as
changes in land use and industrial
development.
Water releases from reservoir proj-
ects serve the multiple purposes not
only of maintaining fish habitat
and the riparian, or streamside
habitat, upon which many birds and
mammals depend, but also of pro-
viding for beneficial consumptive
uses and purposes. Considerable
success has been achieved in ef-
fecting downstream releases in the
Sacramento Basin. This has been
accomplished by agreements usually
negotiated between the construction
agency and the Department of Fish
and Game. At the present time 26
such agreements representing 13
different agencies are in effect.
The streams and quantities are shown
in the tabulation at the bottom of
this page.
In summary, the overall outlook for
sufficiency of water supplies to
meet future demands in the Sacramento
Basin is excellent. Although much
of the Basin will have surplus water,
such surpluses generally are not
transferable because of location,
topography, or other factors, and
certain areas are expected to have
a future deficiency. By and large,
however, proposed local and federal
projects could satisfy these defi-
ciencies. In addition to the water
demands of an expanding agricultural
economy, the Basin will remain an
Stream
Streamflow Releases
(Acre-Feet Per Year)
Upper Sacramento
Pit-McCloud
Sacramento at Keswick Dam
Clear Creek at Whiskeytown Dam
Feather River at Oroville
Feather River Tributaries,
including New Bullards Bar Dam
American River and Tributaries
TOTAL
60,000
150,000
2,000.000
20,000
970,000
290 , 000
390 ,000
3,880,000
-116-
attractive and desirable area for
fish and wildlife and other recre-
ational pursuits.
Delta-Central Sierra Area
The Delta-Central Sierra area con-
tains the Delta of the Sacramento
and San Joaquin Rivers and the
watersheds of the Calaveras,
Mokelumne, and Cosumnes Rivers.
The Delta consists of many islands,
often below sea level, among a maze
of meandering channels . Behind pro-
tective levees, irrigated agricul-
ture has flourished for many years
on the rich peaty soils, which are
especially suited for asparagus
growing. East of the Delta, valley
lands rise gradually for quite a
distance before reaching foothills
which blend into the rugged mountains
of the Sierra Nevada.
The flat valley lands are similar in
appearance and potential use to lands
of the Sacramento Valley to the north
and the San Joaquin Valley on the
south. However, there is more ma-
rine influence due to prevailing
summer winds coming in through the
gap in the Coast Range to the west.
This more moderate climate makes
possible the culture of the famous
Tokay variety of table grape near
Lodi and also the pear orchards
along the Sacramento River in the
Delta.
Estimated I967 agricultural water
demand was 2.3 million acre-feet
per year, of which a little over
half was in the Sacramento-San
Joaquin Delta. Some increase in
irrigated land is expected in the
future, mostly in valley areas sur-
rounding the Delta. As a result,
on-farm water demands are projected
to increase to 2.5 million acre-
feet in 1990 and 2.6 million acre-
feet in 2020.
Water demands for urban purposes are
expected to approximately triple by
2020. Included in the future urban
demand is an allotment of 75,000 acre-
feet of cooling water to be imported
from the American River for the
Rancho Seco nuclear powerplant now
under construction by the Sacramento
Municipal Utility District.
The present (1967) and projected
1990 and 2020 population, land use,
water demands, and estimated water
supplies in the Delta-Central Sierra
area are shown in Figure 25. Fig-
ure 26 illustrates the geographical
distribution of water demands and
supplies.
Major existing surface sources of
water are the Mokelumne River, which
also serves as a supply for the East
Bay Municipal Utility District in
the San Francisco Bay area; the
Calaveras River; and the channels
of the Delta. The amount of water
available from the Mokelumne River
is anticipated to decline somewhat
in the future when full East Bay
Municipal Utility District exports
are made; hence, the reduction in
local surface supply on Figure 25.
In addition, water is served in
areas west of the Delta from the
Putah South, Contra Costa, and Delta-
Mendota Canals. Ground water com-
prises an important source, meeting
over 30 percent of the demand today,
partially at the expense of ground
water overdrafts which aggregate
slightly more than 100,000 acre-feet
in the area east of the Delta. A
major new facility just beginning
construction is the Folsom South
Canal, which would serve a large
area of the valley east of Sacramento,
Lodi, and Stockton.
After allowing for the capabilities
of existing water sources and those
under construction, a deficiency, or
supplemental demand, of about
90,000 acre-feet in 1990 and l80,000
acre-feet in 2020 is forecast for
the Delta-Central Sierra area. These
additional demands would be located
in three areas: (l) Solano County
to the northwest of the Delta;
(2) Contra Costa and San Joaquin
Counties to the southwest of the
Delta; and (3) higher valley, foot-
hill, and mountain regions east of
the Folsom South Canal service
area .
-117-
FIGURE 25
2020
1990
1967
1 URBAN
IRRIGATED
1
1
\ REMAINING
IRRIGABLE
1
I
1
2 4 6 8 10
..1. 'Ill
AGRICULTURAL
URBAN -^
1 2
3 4
1 1 .
100,000 PERSONS
POPULATION
100,000 ACRES
LAND USE
1,000,000 ACRE-FEET
APPLIED WATER DEMANDS
2.5
2.0 -
1.5
.0 -
PROJECTED NET WATER DEMANDS — ^
.
-
'^i ~ "ReauireH Addit.-^-
al Snnnlieo *
_^^;;-s:::==:===^^^^^^^ ""^^^^^^^^ter supplies existing or
^^.,*!*=^- under CONSTRUCTION in 1,000 AF/YR. "
—
1967 1990
Local Surface Water Development 190 160
Ground Water: Safe Yield 570 560
Ground Water: Overdraft 100 0
Central Valley Project, including Delta channel
2020
160
560
0
-
diversions 980 1270
Other Federal: Putah South Canal, New Hogan 90 120
Total Net Supplies 1930 2110
1330
120
2170 —
* Potential additional supply sources: Cosumnes Division, CVP; West Sacramento C
Unit, CVP; New Melones Reservoir, CVP
.1 1 1 1 1
mals
1970
1980
1990
YEAR
2000
2010
2020
PROJECTED WATER SUPPLIES AND NET WATER DEMANDS
DELTA - CENTRAL SIERRA HYDR0L06IC STUDY AREA
-118-
FIGURE 26
DELTA - CENTRAL SIERRA
HYDROLOGIC STUDY AREA
I 1 NET WATER SUPPLY
I 1 NET WATER DEMAND
f^^'HZi SUPPLEMENTAL WATER DEMAND
NOTE: Bar Chorf Units Are Million Acre-Feet Per
r Year /* ) ^ /
J
/
rs / F(
FOOTHILL AND UPLAND
10
m
m
"
/
KEY TO STUDY AREAS
-119-
Eastern Solano County shortages
could be met from the proposed West
Sacramento Canals Unit of the
Central Valley Project, by possible
direct diversion from one of the
Delta channels, or by interim ground
water overdraft pending the con-
struction of an import project.
The supplemental demands of the
strip of valley and foothill lands
southwest of the Delta could be
partly supplied from the proposed
Kellogg Unit of the Central Valley
Project. Those in San Joaquin
County, which are expected to be
almost entirely for farm purposes,
could possibly be met from the
Central Valley Project or from ex-
panded State Water Project sources
via the California Aqueduct.
In the remaining area future
deficiency, east of Folsom South
Canal service area, supplemental
water demands are forecast to be
about 50,000 acre-feet in 199O and
120,000 acre-feet in 2020. A sig-
nificant portion of this demand is
for agriculture and may not materi-
alize unless a relatively low-priced
supply, such as the proposed
Cosumnes River Division of the
Central Valley Project, is available.
A large share of the forecast short-
age could be provided from the
proposed Cosumnes River Division.
It would appear that one upper
reservoir plus Nashville Reservoir
would be adequate for meeting most
local future demands on the Cosumnes
River drainage area.
Additional water demands in the
northern tip of Stanislaus County
could probably be best provided
from the New Melones Project,
possibly via Oakdale Irrigation
District. Supplemental water could
also be made available from El
Dorado County's Central Valley
Project reservation in Folsom Lake,
the Malby diversion from Folsom
Lake, the proposed Swiss Ranch
development in Calaveras County,
and other mountain area small
projects.
The Sacramento-San Joaquin Delta's
700 miles of waterways form a
unique aquatic environment for the
greatest variety of fish and other
aquatic life found anywhere in
California. Substantial populations
of striped bass, salmon, steelhead,
shad, catfish, and sturgeon are
dependent on this area during all
or part of their lives. About 80
percent of California's commercial
salmon fishing depends upon the
Delta estuary in one way or another.
In addition to its local agricul-
tural, industrial, recreational,
and esthetic values, the Delta is
the common point of collection and
diversion of waters southward to
meet the growing water needs of the
San Joaquin Valley and Central and
Southern California.
Water quality has been a problem in
the Delta from the time that low-
lying lands were originally re-
claimed and farming began. In the
past the problems have been caused
primarily by the intrusion of ocean
salinity from the tidal movement,
especially during periods of very
low outflow of fresh water, such as
occurred in 1924 and 1931. During
such low-flow conditions much of
the Delta could not be irrigated
because of the intolerable salinity
in the channels and sloughs which
served as a water supply source.
Summer releases of stored water
from Shasta Reservoir, together
with Folsom and Oroville in more
recent years, have vastly reduced
the salinity intrusion problem. In
fact, no significant intrusion of
salt water has occurred since 19^4
when Shasta Dam was completed.
Water quality problems in the Delta
have been intensified with the in-
creasing discharge of agricultural
drainage and industrial wastes into
Delta channels, expanded use in the
Central Valley, and increasing
export of Central Valley water to
the Bay area. It has been recognized
that these problems will become more
aggravated in the future unless
steps are taken to protect and pre-
serve the Delta environment.
-120-
In studies leading to the State
Water Project, it became apparent
that facilities in the Delta would
be needed to transfer project water
across the Delta without undue loss
or deterioration in quality; to
assure an adequate supply of good-
quality water and protection of
Delta lands from the effects of
salinity intrusion; to protect the
valuable fishery resources of the
Delta, and where possible, provide
for their enhancement. Consequently,
an interagency committee, composed
of representatives of the Bureau of
Reclamation, the Corps of Engineers,
and the Department of Water Re-
sources, examined all previous
plans for a multi-purpose Delta
water facility. The objective was
to recommend a mutually acceptable
plan that would provide for the
various needs of the Delta and
satisfy the needs of the Central
Valley Project and State Water
Project for water transfer. The
committee recommended the Peripheral
Canal plan as the only acceptable
plan of the several alternatives
that could meet the various criteria
considered essential to provide a
suitable environment in the Delta
while simultaneously meeting water
delivery requirements elsewhere.
San Joaquin Basin
The San Joaquin Basin consists of
the entire drainage area of the
San Joaquin River and its tribu-
taries upstream from the San Joaquin
River gage near Vernalis, at the
southerly edge of the Delta.
The average annual runoff of the
Basin is about 6 million acre-feet.
The major streams are the San
Joaquin River and its three major
east side tributaries--the Stani-
slaus, Tuolumne, and Merced Rivers.
In addition, large amounts of water
are imported via the Delta-Mendota
Canal, partly as water exchange,
permitting diversion of San Joaquin
River water at Friant Dam.
As in other parts of the Central
Valley a wide variety of crops can
be grown in the San Joaquin Basin.
The area is noted for its truck,
tomato, fruit, and nut production.
Dairying is also prominent. Ir-
rigation development began in the
1870s with diversions of water
from major rivers. Expansion of
irrigated acreage has continued
at a rate of about 10 to 15 percent
per decade.
Total water applied for all uses in
the Basin in 1967 amounted to
about 5.7 million acre-feet, of
which 5.5 million was for agri-
cultural purposes. Corresponding
total net water use (consumptive
uses plus irrecoverable losses)
was about 4.4 million acre-feet,
which was provided by firm local
and imported surface and ground
water developments, including
depletion of ground water storage
by nearly 200^000 acre-feet.
The rate of irrigated land expan-
sion, as forecast in this bulletin,
is expected to diminish appreciably,
increasing about 25 percent over
present levels by 2020. Due to a
predicted change in crop patterns,
the need for applied water for
farming is forecast to increase at
a much slower rate from an esti-
mated 5.5 million acre-feet at
present to 6 million acre-feet
in 2020.
Urban applied water demands ,
currently about 150,000 acre-feet,
are expected to nearly triple by
2020. Even so, urban water use
will be only about 7 percent of
the total water demand.
Fish, wildlife, and recreation
demands were taken from preliminary
federal-state Framework Study work.
These are primarily for waterfowl
refuges. The San Joaquin Basin
affords important winter waterfowl
habitat, especially in the grass-
lands region near Los Banos . The
projected increase envisions sub-
stantial expansion of federal and
state waterfowl management, areas .
The present (1967) and projected
1990 and 2020 population, land
use, water demands, and water
supplies in the San Joaquin Basin
-121-
FIGURE 27
2020
1990
1967
100,000 PERSONS
POPULATION
~| URBAN
IRRIGATED
t
REMAINING
IRRIGABLE
6 10 14
J I I I I i_
AGRICULTURAL
•^URBAN
^■■
1 3 5
1 1 1 1 1
7
1 1 1
100,000 ACRES
LAND USE
1,000,000 ACRE -FEET
APPLIED WATER DEMANDS
5.0
In 45
4.0
3.5
PROJECTED NET WATER DEMANDS
NET WATER SUPPLIES EXISTING OR UNDER
CONSTRUCTION IN 1,000 AF/YR.
Local Surface Water Development
Ground Water: Safe Yield
Ground Water: Overdraft
Central Valley Project
Other Federal: Hidden and Buchanar
State Water Project
Total Net Supplies
* Potential additional supply sources; East Side Divi
ground water withdrawals from storage.
I I I
1967
1990
2020
2040
2125
2085
580
580
580
170
0
0
1580
1670
1720
Unit, CVP;
I
1970
1980
1990
2000
2010
2020
YEAR
PROJECTED WATER SUPPLIES AND NET WATER DEMANDS
SAN JOAQUIN BASIN HYDROLOGIC STUDY AREA
-122-
FIGURE 28
SAN JOAQUIN BASIN
HYDROLOGIC STUDY AREA
I 1 NET WATER SUPPLY
i~ — 1 NET WATER DEMAND
I 1 SUPPLEMENTAL WATER DEMAND
NOTE: Bar Chart Units Are Million Acre-Feet Per Yeor
KEY TO STUDY AREAS
■123-
are shown in Figure 2J. The geo-
graphical distribution of water
demands and supplies is indicated
on Figure 28. The major share of
the increase in water use is ex-
pected to occur on the southeastern
portion of the valley floor and
along the foothills of the Sierra
Nevada. The slight decrease in the
local surface supply between 1990
and 2020 on Figure 27 is due to
slightly decreased net demand in
major irrigation districts as a
result of projected urban
encroachment.
Existing projects and possibly some
localized additional ground water
pumping are considered adequate to
meet the future needs of the Oakdale,
South San Joaquin, Waterford,
Modesto, Turlock, and Merced Irri-
gation Districts until 2020. West
side supplies appear adequate until
sometime after 1990.
Construction of Hidden and Buchanan
Reservoirs on the Fresno and Chow-
chilla Rivers will provide about
50,000 acre-feet of average yield
annually, and at the same time give
badly needed flood protection to
the Madera and Chowchilla areas.
The water yields from these two
projects will be needed in the
water-short valley floor areas
before 1990.
New Melones Reservoir, now under
construction on the Stanislaus
River, will develop nearly 300,000
acre-feet of yield. Its water
supply will be incorporated into
the Central Valley Project and
could be made available to areas
of need within the Basin if yet
unauthorized conveyance works are
built. In addition to the water
supply aspect, planned fishery and
water quality releases from New
Melones Dam will help to alleviate
existing water quality problems in
the lower San Joaquin River.
Water supplies, mostly small and
widely distributed throughout the
Sierra Nevada, must be developed
to meet the expected additional
upland area needs in 1990 and 2020.
The projected east side valley
floor deficiencies of 300,000 acre-
feet in 1990 and 560,000 acre-^'eet
in 2020 can be met either by tempor-
arily continuing to mine water
from underground storage or by
importing supplemental water into
the Basin. Considering the magni-
tude and location of the deficiencies
in both the San Joaquin and Tulare
Basins, and the probable alignment
of the proposed East Side Canal of
the Central Valley Project, it
appears that importation is the
most practical long-range solution--
most likely via the proposed East
Side Division.
It is possible tha
Canal may permit d
surface supplies i
upland areas where
been inhibited bee
water users hold a
rights. Perhaps e
negotiated in whic
users would be fur
Canal water in exc
stream development
poses . The propos
Canal also has the
improving downstre
in all the signifi
the San Joaquin Ba
t the East Side
evelopment of
n thosp Sierra
development has
ause downstre'^m
11 the water
xchanges could be
h the downstream
nished East Side
hange for up-
for local pur-
ed East Side
potential for
am fishery flows
cant streams of
sin .
Streamflow maintenance agreements
in the San Joaquin Basin provide
water for diverse fish and wildlife
needs. In the San Joaquin and
Stanislaus Rivers, the flows pro-
vide for trout stream habitat that
would be otherwise depeleted
through diversion for power devel-
opment, irrigation, and domestic
use. The Merced River flows are
utilized for salmon and steelhead
spawning. The purpose of the
agreements with the U. S. Bureau of
Reclamation is to mitigate the loss
of waterfowl habitat inundated by
the San Luis and Los Banos
Reservoirs .
Several local agencies and the
U. S. Bureau of Reclamation have
signed agreements with the
California Department of Fish and
Game for streamflow releases as
shown in the tabulation at the top
of the next page.
-124-
stream
San Joaquin
Merced
Stanislaus
Los Bancs -
San Luis
Agency
Southern California Edison Company
Merced Irrigation District
Tuolumne County Water District No.
Oakdale and South San Joaquin
Irrigation District
Calaveras County Water District
U. S. Bureau of Reclamation
Streamflow Releases
(Acre-Feet Per Year)
^3,000
M3,000
168,000
i|,000
The Corps of Engineers is studying
flood problems throughout the San
Joaquin Basin. Current studies in-
clude the Merced Stream Group.
Tulare Basin
The Tulare Basin compri
entire drainage area of
Joaquin Valley south of
Joaquin River. It is g
ficient in natural wate
yet, in contrast, it is
agricultural producer i
Satisfaction of water d
the Basin, which are th
of the 11 hydrologic st
relies to a considerabl
imported supplies and g
overdraft .
ses the
the San
the San
rossly de-
r resources;
the largest
n the State,
emands in
e greatest
udy areas,
e extent on
round water
Natural water supplies of the Basin
are derived primarily from Sierra
Nevada runoff in the Kings, Kaweah,
Tule and Kern Rivers. These
streams provide a source for direct
diversion for agricultural and
urban uses and also replenish the
underlying ground water basin by
direct percolation from channels
and from the unconsumed portion of
applied waters.
Use of water in the Tulare Basin has
long exceeded the natural water
supplies, and supplemental supplies
have been imported via the Friant-
Kern and Delta-Mendota Canals of
the federal Central Valley Project.
In 1967 the total amount of all
water available for firm and sus-
tained use in the Basin averaged
about h .6 million acre-feet, while
the net use of water amounted to
about 6.h million acre-feet. The
excess of use over available firm
supplies is met by a long-term
average annual net depletion of
ground water of about 1.8 million
acre-feet .
Currently, the State Water Project
and the San Luis Unit of the
Central Valley Project are deliv-
ering water to the Basin. Under
full delivery those two projects
will provide a total of about
2.6 million acre-feet annually.
However, even with local develop-
ments and these large import
projects operating at full con-
tractual opacity, the Basin's
economy is expected to grow to
such an extent that the annual
water demand in excess of its
existing combined yield will be
about 1.2 million acre-feet by
1990 and about 2.1 million acre-
feet by 2020. This growth in
economy is projected on the basis
of the extremely favorable combin-
ation of soils and climate and
advantageous market location for
a thriving agricultural industry.
The geographical distribution of
present and projected supplemental
water demands is important in the
consideration of likely water
sources to meet the total water
needs of the Tulare Basin. Supple-
mental water needs west of the
valley trough could be served by
additional deliveries from the
San Luis Unit of the Central Valley
-125-
FIGURE 29
2020
1990
1967
2
"1 URBAN
IRRIGATED
1,000,000 PERSONS
POPULATION
1,000,000 ACRES
LAND USE
AGRICULTUrtAL
2 4
URBAN'
10 12 14
1,000,000 ACRE- FEET
APPLIED WATER DEMANDS
NET WATER SUPPLIES EXISTING OR
UNDER CONSTRUCTION IN 1,000 AF/YR.
1967
1990
2020
Local Surface Water Development
2290
2290
2290
Ground Water: Safe Yield
500
600
600
Ground Water: Overdraft
1800
0
0
Central Valley Project
1460
2690
2690
Other Federal: Pine Flat, Success, Ter
ninus, Isabella
240
240
240
State Water Project
0
1350
1350
Total Net Supplies
6390
7170
7170
1970
1980
2010
1990 2000
YEAR
PROJECTED WATER SUPPLIES AND NET WATER DEMANDS
TULARE BASIN HYDROLOGIC STUDY AREA
2020
-126-
FIGURE 30
TULARE BASIN
HYDROLOGIC STUDY AREA
I 1 NET WATER SUPPLY
I 1 NET WATER DEMAND
I 1 SUPPLEMENTAL WATER DEMAND
NOTE: Bar Chart Units Are Million Acre-Feet Per Yeor
UPLANDS
I
rpi
-|
1967 1990 2020
\
-
I]
-
-
\
i
KEY TO STUDY AREAS
X
1967 1990 2020
>Vn
^
V-
I
c^ -''
V^
r
r
3
-127-
Project and the State Water Project.
These deliveries would initially be
needed around 1990 and are estimated
to increase to about 5OO5OOO acre-
feet annually by 2020. While the
California Aqueduct could trans-
port the additional water with
relatively inexpensive augmentation
of capacity, this water service is
not included in present contracts.
Supplemental water service for the
eastern slope of the valley floor
could be provided by a project
such as the proposed East Side
Division of the federal Central
Valley Project. East Side delivery
requirements are projected to be
about 1.2 million acre-feet in
1990 and about 1.6 million in 2020.
Whereas presently contracted sup-
plies from the federal San Luis
Unit and the State Water Project
appear sufficient to serve the west
side of the valley floor until
about 199O) the easterly slopes of
the valley floor are in need of
supplemental water now, and a rapid
buildup in use of imported supplies
is anticipated when they become
available from the East Side
Division.
Preliminary economic studies indi-
cate that at the proposed canalside
prices the water users could real-
ize significant savings in their
total water cost if the full deliv-
ery capacity of the East Side
Project were utilized at an early
date. This would enable the ground
water basins to refill, thereby
decreasing the unit pumping costs
for the remaining large amount of
ground water which still must be
pumped to meet the total applied
water demand within the area.
Further examination should be made
of the possible economic and oper-
ational advantages of fully co-
ordinated operation of the existing
and future surface and ground water
resources of the Tulare Basin.
This should include the effects of
continuing to draw upon the ground
water basin and the operational
flexibility which could be obtained
for the major aqueduct systems if
the east and west side projects
were joined either physically or
by exchange agreements.
Full realization of the economic
potential of the Basin would also
require future construction of the
San Joaquin Valley master drain to
avoid crop losses and serious
degradation of the ground water.
With regard to fish and wildlife,
streamflow maintenance agreements
in the Kern River drainage cover
flow releases below various power
diversions of the Southern
California Edison Company system.
The stipulated flows include about
l4,000 acre-feet annually for a
water supply to the Kern River
Fish Hatchery at Kernville. Kings
River water releases maintain flows
below Pine Flat Dam. Stabilized
flows in the Kings have permitted
development of a popular year-
round trout fishery, including a
special fly-fishing season during
the winter.
While the principal tributary
Sierra Nevada streams have major
reservoirs that provide downstream
flood protection in most years,
intense rainfall (such as occurred
over the Kaweah River watershed in
the winter of I968-69) or the
combination of warm weather or an
extremely deep snowpack, which
resulted in severe flooding in the
Tulare Lake bed in January 1969
still posesa serious flood threat.
The U. S. Army Corps of Engineers
is conducting a basin-wide study
on water resources development and
flood problems in the entire San
Joaquin Valley. The Corps is also
assisting local agencies in flood-
plain management through the prep-
aration of floodplain information
reports .
In summary, it appears that because
of the location of the Tulare Basin
with respect to potential water
supply sources, future increases in
water demand could most logically
be served by federal and state
project facilities which already
-128-
have the capacity to deliver some
4 million acre-feet annually to
the area.
The supply-demand relationships
for the Tulare Basin from the
present (1967) to 2020 are illus-
trated graphically in Figure 29
and geographically in Figure 30.
North Lahontan Area
The North Lahontan area is the
narrow strip of State lying east
of the Sierra Nevada along the
California-Nevada border. It
extends approximately 270 miles
from the vicinity of Bridgeport in
Mono County to the Oregon border.
The economy is dependent upon agri-
culture, recreation, lumbering and
mining. The principal agricultural
activities are livestock production
and forage crops. Lake Tahoe and
vicinity provides the stimulus for
year-round recreation important to
the area's economy.
While the total annual runoff ex-
ceeds present water demands, lack
of streamflow regulation and carry-
over storage contribute to water
shortages during part of the full
irrigation season. With possible
minor exceptions, paucity of eco-
nomical reservoir sites preclude
surface water development from
serious consideration in the future.
In recent years, increased use of
ground water has partially alle-
viated seasonal irrigation short-
ages. The trend is expected to
continue, prompting concern from
local interests regarding the lack
of adequate knowledge of the safe
yield of the various ground water
basins .
Total irrigated acreage in the
North Lahontan area is not ex-
pected to increase in the future;
but an anticipated change in crop
patterns is expected to increase
the total agricultural water de-
mand, creating shortages in water
supplies amounting to 30,000 acre-
feet by 1990 and 50,000 acre-feet
by 2020. The water demand-water
supply relationship is illustrated
in Figure 31 and geographically in
Figure 32.
The tremendous recent growth in
recreation development within and
adjacent to the Lake Tahoe Basin
is expected to continue. It is
estimated that there will be a
fourfold increase in total summer
population by 2020. This assumes
no restrictions other than land
availability. In this regard, the
Lake Tahoe Regional Planning Agency
was recently created to control
land use in that Bpsin. The land
development policies that may
emanate from this agency could
result in a different mode and
level of development than was
projected in this study.
Water demands propagated from
urban recreation development can be
met by supplies until sometime after
1990. By 2020 the supplemental
water demand would be about 70,000
acre-feet, of which 60,000 acre-
feet would be in the Lake Tahoe-
Truckee River Basin. Water use
by the permanent population is,
and will continue to be, only a
small portion of the total urban-
recreational water demand. Possible
me.Tns of meeting this future sup-
plemental demand have not been
identified. Estimates of available
future supplies were based largely
on U. S. Bureau of Reclamation
feasibility reports and the pro-
posed California-Nevada Interstate
Compact. The authorized Stampede
Unit of the Washoe Project was
considered a part of the available
supply.
The California-Nevada Interstate
Compact divides the waters of Lake
Tahoe and Truckee, Carson, and
Walker River Basins. The proposed
compact was ratified by the
California Legislature in amended
form at the 1970 session. It is
hoped that the amended contract
will be ratified by the Nevada
Legislature in 1971 so that it may
be submitted to the Congress for
approval during the next session.
-129-
FIGURE 31
2020
1990
1967
1 URBAN
1 IRRIGATED
REMAINING IRRIGABLE 1
1
I
1
1
I
1
12 3 4 5
1 1 ' 1 1
1,000 PERSON
POPULATION
100,000 ACRES
LAND USE
AGRICULTURAL
URBAN
-f-
100,000 ACRE-FEET
APPLIED WATER DEMANDS
.5 —
.4 —
.3 —
PROJECTED NET WATER DEMANDS-^^^^ ^^
-
^^^^^ Required Addi
tional Sl
pplies*-
^^^^......-.^--'''''^^l]^---^^ WATER SUPPLIES EXISTING
OR
-
""""^ ^^-""^ UNDER CONSTRUCTION IN
1000
AF/YR.
1967
1990
2020
—
Local Surface Water Development 290
Ground Water SO
Tule Lake Import 10
Stampede ^
Total Net Supplies 350
320
110
10
10
450
320
140
10
10
480
♦Potential additional supply sources: Local streams development. Sierra tunnel di
1 1 1 1
1
1970
1980
1990
YEAR
2000
2010
2020
PROJECTED WATER SUPPLIES AND NET WATER DEMANDS
NORTH LAHONTAN HYDROLOGIC STUDY AREA
-130-
FIGURE 32
NORTH LAHONTAN
HYDROLOGIC STUDY AREA
NET WATER SUPPLY
NET WATER DEMAND
SUPPLEMENTAL WATER DEMAND
<
\
/lassen group i^
t . . . . .
0.3
0 2
0,1
0
T-
na
1967 1990 2020
KEY TO STUOT 4HE4S
V
Nl
V
NOTE: Bar Chart Units Are Million Acre-Feet Per Yeor fj I
f
V
ALPINE GROUP
0 3
0.2
01
n
!
'
r^HHOE
1967 1990 2020
X
SCALE OF MILES
0 a 16 24
y
-131-
DWR employee
North Lahontan Area
— nciture provides ample wiiter resources, hut in^ullicienl carryover storage
to meet lull summer demands
Briefly, the allocation of water
to California consists of (l) the
right to divert 23,000 acre-feet
per year for use in the Lake
Tahoe Basin; (2) recognition of
existing exports from the Lake
Tahoe, Truckee River, and
Walker River Basins; (3) the right
to divert 10,000 acre-feet per
year for use within the Truckee
River Basin, the right to deplete
the 6,000 acre-feet of the annual
yield of Stampede Reservoir, and
the right to develop and deplete
an additional yield of 10,000 acre-
feet from the Truckee River and
Lake Tahoe Basins, if available;
(4) the right to divert water to
irrigate approximately 5,600 acres
along the West Fork of the Carson
River and 3,820 acres along the
East Fork of the Carson River, to
develop by storage 2,000 acre-feet
of water per annum in Alpine
County, and to develop for use in
California 20 percent of the re-
maining water after the foregoing
California users and existing
users in Nevada have been supplied;
and (5) recognition of existing
rights and uses in the Walker
River Basin plus the right to
develop 35 percent of the remaining
water after Nevada's existing
rights and uses are satisfied. In
addition, ground water and springs
may be used in the Truckee, Carson,
and Walker River Basins provided
such use does not reduce the
amount of water which Nevada would
otherwise receive under the
allocation.
In addition to water supply-water
demand inequalitites , the North
Lahontan area has other problems
related to its areal growth and
development, namely flood control
and water quality.
The whole area is periodically
subjected to widespread storms and
subsequent flooding. Aside from
the normal November to April
season for rain floods , snowmelt
in late spring can cause damage
during exceptional snowpack years.
Damage areas occur principally
along the Truckee and Walker
Rivers, the Susan River in Surprise
Valley and in the community of
Susanville, and communities along
the shore of Lake Tahoe. Only
5 percent of the area subject to
flooding now has protection by
structural measures. Scattered
damage centers for the most part
will preclude project justification
in the future. The most logical
means to mitigate flood damages
would be through regulation of
floodplain use to limit encroach-
ments in active floodways and an
improved flood warning system.
Water quality problems have arisen
in recent years due to waste dis-
charges into Lake Tahoe. This
problem has been partially solved
by exporting treated sewage out of
the Tahoe Basin into Indian Creek
Reservoir near the town of Woodfords
in the Carson River Basin. Studies
are now under way to find a solu-
tion to the problem of waste dis-
charges in the North Tahoe Basin.
Any solution to this problem will
be complex because of the implica-
tion of water rights, as well as
the physical plan of waste disposal.
South Lahontan Area
The South Lahontan area encompasses
the portion of Lahontan Hydrologic
Drainage Province from Mono Lake
south and is characterized by a
large number of enclosed basins and
sinks. It has the greatest ex-
tremes in elevation within the
contiguous United States, ranging
from 282 feet below sea level in
Death Valley to 1^,495 feet above
sea level on Mount Whitney, only
80 miles distant.
The economic development of the
area as a whole was slow in the
1960s but has begun to quicken
recently in the Antelope Valley
and south of Victorville in San
Bernardino County. Lockheed Air-
craft Corporation provided the
recent stimulus by building a plant
just northeast of Palmdale and
began the manufacturing of air buses
in 1969. The planned Palmdale
-133-
FIGURE 33
2020
1990
1967
2
1
4 6 8 10 12
1 1 1 1 1
100,000 PERSONS
POPULATION
I
URBAN
IRRIGATED
REMAINING IRRIGABLE
20 24
_I L.
100,000 ACRES
LAND USE
\
URBAN
AGRICULTURAL
100,000 ACRE-FEET
APPLIED WATER DEMANDS
PROJECTED NET WATER DEMANDS
NET WATER SUPPLIES EXISTING OR
'UNDER CONSTRUCTION IN 1000 AF/YR.
Local Surface Water Development
Ground Water: Safe Yield
Ground Water Overdraft
State Water Project
Total Net Supplies
♦Potential additional supply sources: Ground water withdrawals from storage, exchanges.
1 1 ! I L__
140
140
140
240
30
45
0
420
210
460
215
490
1970
1980
1990
YEAR
2000
2010
2020
PROJECTED WATER SUPPLIES AND NET WATER DEMANDS
SOUTH LAHONTAN HYDROLOGIC STUDY AREA
-13^-
FIGURE 34
SOUTH LAHONTAN
HYDROLOGIC STUDY AREA
NET WATER SUPPLY
NET WATER DEMAND
SUPPLEMENTAL WATER DEMAND
NOTE: Bar Chart Units Are Million Acre-Feet Per Year
■135-
Intercontinental Airport will
provide another stimulus. The
impact of this airport will be
considerable reaching into Kern
County to the north and into San
Bernardino County to the east.
Construction of the first runway
is expected to begin in 1973 and
to be ready for the first flight
scheduled in 1977- The number of
passengers to be handled is pro-
jected to grow from 1 million in
1980 to 50 million by 2000.
Plans for an additional freeway
and a mass rapid transit system
connecting the Antelope Valley with
Los Angeles have been discussed by
various agencies. The airport will
employ several thousand people
directly and create many Jobs in-
directly through related industries
and services, which will result in
a greatly increased population of
the Antelope Valley. Consequently,
some irrigated agriculture may move
from Los Angeles County to Kern
County in the South Lahontan area.
Economic development of the south-
ern part of Kern County around the
community of Mojave also will be
generally enhanced.
The western strip of Victor Valley
bordering Los Angeles County will
also undergo development; but the
recently started subdivision
activity in western San Bernardino
County in the vicinity of Victor-
ville is largely independent from
the planned Palmdale Intercontinen-
tal Airport. Two large real estate
developments at Spring Valley Lake
and at the southern outskirts of
Victorville are geared, at least
in part, toward providing second
homes and retirement homes.
Agricultural water demand of the
area is anticipated to remain
approximately the same until 1990
and to diminish slightly there-
after, due to the anticipated
urbanization centered around Palm-
dale. The total net water demands
are estimated at about 420,000 acre-
feet per year in I967 and 500,000
acre-feet in 2020.
The South Lahontan
for discussion purp
Mono-Owens Valley,
area, encompassing
area from Indian We
Nevada, and the Ant
Mojave River area,
tude and geographic
of water demand and
area are illustrate
and 34.
area is divided
OSes into the
the Death Valley
the huge desert
lis Valley to
elope Valley-
Relative magni-
al distribution
supply in the
d in Figures 33
In the Owens
Los Angeles
will be a su
available in
to meet urba
mands and al
irrigation s
18,000 acres
out endanger
supplies to
a critically
Valley, the City of
estimates that there
fficient water supply
the Mono-Owens Valley
n and recreational de-
so to provide a firm
upply for approximately
of agriculture with-
ing the integrity of
the City, even during
dry period.
In recent years, the City exported
over 3^0^000 acre-feet per year--
the full capacity of the first
aqueduct. A parallel aqueduct com-
pleted in June 1970 increased the
total export from the area to about
510,000 acre-feet annually. This
yield and the firm local water
supply will be obtained from oper-
ation of the Owens Valley ground
water basin in conjunction with
surface supplies from the Owens
River and the streams of Mono Basin.
Water supplies for local use in the
area outside the Mono-Owens Valley
will come from local ground water
basins. However, there are limited
amounts of water available from
surface diversions. Currently, the
use of ground water exceeds the
annual replenishment of the basins
by an estimated 240,000 acre-feet,
resulting in falling ground water
levels .
The estimated water demands for
the Antelope Valley-Mojave River
area also include those of Lucerne
Valley which is included in the
Mojave Water Agency even though
physically located in the Colorado
Desert area. In 1972 Antelope
Valley-East Kern, Crestline-Lake
-136-
Arrowhead and Mojave Water Agencies
and Palmdale and Littlerock Irriga-
tion Districts (in the Antelope
Valley-Mojave River area) will
begin receiving water from the
State Water Project; their maximum
entitlement is 215,000 acre-feet
per year.
The water supply estimates on
Figure 33 assume a 10 ,000-acre-foot
per year safe supply in the Death
Valley area. The safe yield has
not been determined for this large
desert region, so that figure must
be regarded as approximate. The
continuing overdraft shown in Fig-
ure 3h in 1990 and 2020 represents
the amount that the Death Valley
area demands will exceed the as-
sumed 10,000-acre-foot safe yield
supply. No reasonable alternative
to the use of ground water in
storage seems apparent for this
area.
There are possible alternatives
for meeting future demand for water
in the Antelope Valley-Mojave River
area. These are (1) continuation
of the depletion of ground water in
storage; (2) purchase of additional
farm supplies from an expanded
State Water Project; and (3) in-
terim use of available capacity in
the California Aqueduct to augment
ground water in storage '"or with-
drawal at a later time. The first
and third alternatives, however,
can be considered only as interim
measures .
In summary, the Mono-Owens Valley
has adequate water supplies to
meet its urban and recreational
demands and also to provide a firm
irrigation supply for about l8,000
acres of agriculture. The Death
Valley area and the Antelope Valley-
Mojave River area will continue to
be water deficient. Demands in
the Death Valley area in excess of
the estimated annual safe ground
water yield of 10,000 acre-feet
are expected to be met from con-
tinued extraction of ground water
from storage. Importation of
State Water Project contractual
supplies will not completely sta-
bilize falling ground water levels
in the Antelope Valley-Mojave River
area, particularly in 1990- and a
demand for supplemental water will
continue. The water demand-water
supply relationships in these areas
are depicted in Figure 3^-
Colorado Desert Area
The Colorado Desert area occupies
the extreme southeastern portion of
California, encompassing Imperial
County and portions of San Diego,
Riverside, and San Bernardino
Counties. The main geographic
features are the Colorado River and
Salton trough containing the Salton
Sea and Imperial and Coachella
Valleys. The area drains into the
Colorado River and into the Salton
Sea, the lowest part of a closed
basin.
The Colorado Desert area is char-
acterized by the driest climate in
the State along with generally mild
winter and very high summer temper-
atures. This area has not enjoyed
a rapid urbanization because of its
extreme summer temperatures and its
distance from metropolitan centers.
The lack of higher-paying employment
opportunities also has contributed
to the slowness of its growth.
However, the area has become popak-rts
a retirement and recreational
center.
Much of the area in the Salton
trough is below sea level and vir-
tually frost -free which permits the
growing of agricultural crops
throughout the entire year. This,
along with availability of low-cost
water, has enabled the development
of an irrigated agricultural economy
second only to the vast Central
Valley area. Because of the sub-
stantial remaining amount of land
that could be developed, urbanization
is not likely to curtail irrigated
acreage.
Although the quantities of water
used for recreation are small, water-
related recreational activities
have increased in the Colorado
Desert area in recent years. Salton
Sea has become an increasingly
-137-
FIGURE 35
2020
1990
1967
1 f
3
4 5 (
1 •
5
100,000 PERSONS
POPULATION
1 URBAN
n.
IRRIGATED
REMAINING IRRIGABLE
1
2 3 4
J I L
^ T ?
100,000 ACRES
LAND USE
AGRICULTURAL
URBAN
-y-
1,000,000 ACRE -FEET
APPLIED WATER DEMANDS
4.2
4.0 —
3.8 —
o 3.6
34 —
PROJECTED NET WATER DEMANDS-^ •
Reomred Additional SuDolies •
—
^— ' -1 —
"■^-^NET WATER SUPPLIES EXISTING OR UNDER
CONSTRUCTION IN 1,000 AF/YR.
—
-
—
1967 1990 2020
Ground Water: Safe Yield 60 60 60
Ground Water: Overdraft 90 20 60
Colorado River Diversions 3830 3850 3850
0 80 80
Total Net Supplies 3980 4010 4050
—
Potential additional supply sources: Geothermal desalination, Salton Sea, desalination, _
xchanges, ground water withdrawals from storage.
1 1 1 1 1
1970 1980 1990 2000 2010 2020
YEAR
PROJECTED WATER SUPPLIES AND NET WATER DEMANDS
COLORADO DESERT HYDROLOGIC STUDY AREAS
COLORADO DESERT
HYDROLOGIC STUDY AREA
FIGURE 36
I I NET WATER SUPPLY
iT"^ NET WATER DEMAND
( I SUPPLEMENTAL WATER DEMAND
NOTE: Bar Chart Units Are Million Acre-Feet Per Yea
■ ^
KEY TO STUDY AREAS
Much of the Colorado Desert's Valley
floor looked like this to the "old-timer".
Now. agriculture is important to
the area — —
grapes with date garden in background
And. of course
J urbanites find fun in the sun, too
Urvi - Division o) Hiqhv.
popular recreational area for the
populous Southern California
coastal cities. A federal-state
reconnaissance report of October
1969, "Salton Sea Project,
California", stated that the Sea
presently has a use rate of I.5 mil-
lion recreation-days annually. The
report also stated that related
public and private investments
total more than $900 million. How-
ever, the recreational value and
its attendant investment value will
diminish considerably unless mea-
sures are taken to control the
increasing salinity of the Sea.
The Colorado River also provides
excellent recreational opportunities
to Southern Californians and others
because of warm winters, picturesque
settings, and ample opportunities
for boating, water skiing, and
fishing. Growth of recreational
activities along the river is
expected to be consistent with the
general population and economic
growth in Southern California.
The total water demands of the area
are projected to increase from
3,980,000 acre-feet per year in
1970 to i;,l40,000 acre-feet in 2020.
Four agencies in the area--the Palo
Verde and Imperial Irrigation
Districts, Yuma Project Reservation
Division, and Coachella Valley
County Water District--have usable
annual diversion rights to
3,850,000 acre-feet of Colorado
River water, according to the
Seven-Party Agreement of August 18,
1931. The decision of the U. S.
Supreme Court in Arizona vs.
California and the Colorado River
Basin Project Act will make it
possible for diversions to continue
at that level. In addition to
Colorado River water, more than
100,000 acre-feet of ground water
is used, mostly in Coachella Valley.
Colorado River water available to
California historically has had a
relatively high salt content. From
1963 to 1967 it averaged 7^0 ppm of
dissolved minerals at Parker Dam
and 850 ppm at Imperial Dam, where
diversions to the irrigation
districts are made. This has re-
quired the installation of exten-
sive networks of tile drains and
the application of quantities of
water considerably in excess of
the actual requirements for plant
growth to prevent salt buildup
and ensure continued successful
farming operations.
The quality of the river water
varies from season to season, de-
pending chiefly on its flow and
the effects of various upstream
uses. Projections of the future
quality of Colorado River water
were made recently by the Colorado
River Board of California. These
projections were based on estimated
effects or the presently authorized
and planned projects in the Basin.
They indicate that unless correc-
tive measures are taken the average
salinity of river water at Imperial
Dam will increase to 1,3^0 ppm by
2000. Under these circumstances
some crops, which are marginal with
today's salinity, could no longer
be grown. If salinity control
projects mentioned in the report
were implemented, it was estimated
that average salinity at Imperial
Dam could be held to about
1,000 ppm.
Salinity at Imperial Dam also
varies substantially from month to
month, with the greatest concentra
tions occurring during the winter.
In some recent years the peak
salinity has exceeded 1,000 ppm.
This has had an adverse effect on
the germination of seeds for
winter-planted crops.
The quality of ground water in the
Coachella Valley is surprisingly
good. Dissolved minerals in the
area are generally less than 200 ppm.
Small amounts of ground water used
in the Palo Verde Irrigation District
have dissolved minerals in excess of
800 ppm, reflecting the quality of
Colorado River water used for
irrigation in the area.
The quality of ground water in the
Imperial Valley is considered to be
■141-
unsuitable for domestic and irriga-
tion purposes except for a few
isolated areas. This has limited
the use of ground water in the
area to extremely small amounts.
The Coachella Valley County Water
District, the Desert Water Agency,
and the San Gorgonio Pass Water
Agency have contracted with the
State for a maximum annual entitle-
ment of 80,000 acre-feet of State
Water Project water. These agencies
are all located in the Coachella
Valley vicinity. However, even
with the addition of this water
the demand for supplemental water
is expected to continue and may be
met by the use of ground water in
storage, as has been done in the
past; by supplemental supplies
from the State Water Project; or
by water from other potential
sources. For other areas where a
demand for supplemental water is
expected to exist and there are no
proposed plans for imported water,
it is anticipated that this demand
will be met by ground water
storage depletion.
The water demand and supply rela-
tionships in the Colorado Desert
area are illustrated in Figures 35
and 36.
Regional Water Demand-
Water Supply Summary
Present (I967) and future (1990
and 2020) water demand and supply
relationships for each of the 11
hydrologic study areas and the
state total are summarized in
Table 8 . The total net water
demands shown as the first item
represent the requirement for de-
veloped water, whether from local,
imported, or other sources. The
total net water supplies represent
the sums of all sources of water,
both local and imported (including
facilities under construction) ,
available toward satisfying net
demands .
Note in Table 8 that sa^'e ground
water yield is included within the
dependable water supplies, but that
ground water overdraft is also
included as a source of supply at
the present (I967) time for several
areas. In most cases such over-
draft is considered to be only an
interim source and is assumed to
be phased out by 1990. However,
there are exceptions in the Central
Coastal area and for localized
situations in the South Lahontan
and Colorado Desert areas where
ground water is the only source of
water supply. In these cases,
ground water overdraft was assumed
to continue indefinitely.
It is anticipated that local agencies
will provide 20 to 25 percent of
the increased dependable water
supplies between the present time
and 2020. This includes additional
surface developments, increased
ground water use, and reclamation
of waste water and represents
essentially full development of
the available local water supplies.
In addition, local agencies will
play a key role in the construction
of distribution systems to deliver
water from state and federal, as
well as, local water projects.
The indicated shortages shown in
Table 8 represent the quanti-
ties of water that must be made
available over and above the net
water supplies to fully satisfy
the indicated net demands. Finally,
the table lists potential supply
sources that might prove feasible
for development in the future.
The water demand-water supply
relationships for each of the
11 hydrologic study areas are
summarized graphically in
Figure 37.
-142-
FIGURE 37
PRESENT AND PROJECTED
WATER DEMAND -WATER SUPPLY RELATIONSHIPS
IN MILLION ACRE - FEET
HYDROLOGIC STUDY AREAS
NC -
SF -
cc -
sc -
SB -
DC -
SJ -
TB -
NL -
NORTH COASTAL
SAN FRANCISCO BAY
CENTRAL COASTAL
SOUTH COASTAL
SACRAMENTO BASIN
DELTA- CENTRAL SIERRA
SAN JOAQUIN BASIN
TULARE BASIN
NORTH LAHONTAN
SOUTH LAHONTAN
COLORADO DESERT
I I NET WATER DEMANDS
AVAILABLE WATER SUPPLIES
1970 1990 2020
-14 3-
ti O
LU — *
:; o
8
O
i
8 SJ
I
I
s s
8 .
-^ 5)
R R
^
3 S
a
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~^
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a e
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SIS ss
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III I
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sag
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Si S5&I
(0 O (D ^ C ^
+> '^ 5 M
o "Si to ^
3«?
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as
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58.^
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S t-^l^ 5
O « Q O
-144-
e §,
s s
ggSSSSSR g I
g 5 .
S 3 .
s s .
S S 3
« § °
g R 3
S &
» S R
§■11
R R
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S B
g 1
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g §
s
S S
i ^
as
as
5^ 5 H C
•3 m
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° g R ^&
Is
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5:s I
= ^11 g
? s 3 s '5 I
« If w >,
a p Q 1- X)
O Si -3 Ml -P
*§ <0 "" C >< M
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ID 41 *5 H TJ
:^-sr)-^, ^i;^
-1^5-
CHAPTER VII . MEETING WATER DEMANDS THROUGH
CENTRAL VALLEY PROJECT AND
STATE WATER PROJECT FACILITIES
The California Water Plan and
subsequent reports of the Department
of Water Resources were published to
provide a basic planning framework
for ensuring that the State's long-
range water demands are met. Two
major multi-purpose projects systems
which are presently fulfilling this
general objective and which possess
the potential for continuing to do
so to an increasing extent in the
future are the Central Valley Proj-
ect of the U. S. Bureau of
Reclamation and the California
State Water Project, currently
nearing completion by the Department
of Water Resources.
These two developments are unique in
their utilization of the coordinated
systems approach to interbasin water
resource preservation and management.
In essence this operational princi-
ple, including the utility and
pooling concepts employed by the
State Water Project, makes possible
the future extension of water ser-
vices to areas of California which
could neither physically nor eco-
nomically be provided by smaller
local or independently operated
developments alone, or from other
alternative sources.
This chapter presents information
concerning the present and potential
future water supply, recreation,
flood control, and water quality
control accomplishments of the State
Water Project and the Central Valley
Project and the advantages of
their coordinated operation. With
regard to the future, it is rec-
ognized that water demands over and
above those to be satisfied by
existing or authorized facilities
of the Central Valley Project or
State Water Project may not be met
exclusively or even principally by
future additions to those projects.
Other potential alternative sources
described in Chapter V may well
play a substantial role in meeting
future demands in areas that could
be served by these projects. The
means of satisfaction of future
water demands remains to be deter-
mined; but because of the indicated
slower rate of buildup in demand
discussed in Chapters IV and VI,
there is time to make such
determination.
However, the assumption is made for
purposes of this chapter that future
water demands in areas that could
logically be served by state and
federal projects will be met by
expansion of those projects. This
procedure serves to illustrate the
operational characteristics and
flexibility of the Central Valley
Project and State Water Project,
including exchange potentials and
the forecasted timing of need for
additional conservation and
transportation facilities.
The Central Valley
Project
The Central Valley Project was
federally authorized for construc-
tion in 1935 under provisions of
the Emergency Relief Act and as a
federal reclamation project in 1937-
In 1967 the project celebrated its
twenty-fifth anniversary of pro-
viding water service via the Contra
Costa Canal, an initial unit of the
Delta Division. This project marked
the beginning of a new phase of
water development in the Central
Valley, as development in various
parts of the Valley had been largely
independent of each other prior to
its initiation. However, use of
water had reached a stage where any
additional facility in one part of
the Valley affected existing and
possible future development elsewhere.
Hence the need for a truly compre-
hensive and fully coordinated
-147-
interbasin development program was
recognized and undertaken through
construction of the federal Central
Valley Project.
Major reservoirs of the Central
Valley Project completed or under
construction include Lake Shasta on
the Sacramento River, Folsom Lake
and Auburn Reservoir on the American
River, Millerton Lake on the San
Joaquin River, and New Melones
Reservoir on the Stanislaus River.
Major aqueduct systems serving ag-
riculture and industry in the Valley
are the Delta-Mendota Canal, Friant-
Kern Canal, Madera Canal, Contra
Costa Canal, Folsom South Canal,
Tehama-Colusa Canal and the Corning
Canal. Other key features of the
Central Valley Project are the San
Felipe Division, Trinity Division,
and the San Luis Division. The
latter consists of San Luis Reser-
voir in western Merced County and
the San Luis Canal, which are joint
features with the California State
Water Project. The total cost of
the Cent];'al Valley Project to date,
including constructed and authorized
features, is on the order of $2.6
billion. These major facilities
are shown on Figure 38.
Current annual water deliveries
under the Central Valley Project
total some 6 million acre-feet. By
about 1990 project water deliveries
are anticipated to be some 10. 7 mil-
lion acre-feet to meet the in-
creasing demands for new and supple-
mental water supplies within the
service areas of the Central Valley
Project. These annual demands are
projected to grow by an additional
2 million acre-feet between 1990
and 2020. Authorization and con-
struction of additional Central
Valley Project facilities, princi-
pally the East Side Division and
the West Sacramento Canals Unit,
would be needed to provide this in-
crease in water deliveries.
While the initial features of the
Central Valley Project have been
virtually completed and other facil-
ities have been authorized and are
under construction, the project is
nevertheless anticipated to continue
to evolve over the next quarter
century to meet the demands within
its service areas on an orderly and
timely schedule. Priority additions
include extension of the project's
transportation systems--namely , the
East Side Division Aqueduct System
and the West Sacramento Canals, and
the joint federal-state Peripheral
Canal. These and other proposed
additions to the Central Valley
Project will be discussed in
subsequent sections of this chapter.
The State Water Project
In 1951 the California Legislature
authorized the Department of Water
Resources to construct the Feather
River Project, later designated the
State Water Project, to conserve
surplus water supplies in the north-
ern portion of the State in excess
of local needs and to convey those
supplies to areas of deficiency in
Central and Southern California.
The Project was designed to provide
other water services in the cate-
gories of flood control, hydroelec-
tric power generation, water-oriented
recreation, salinity control in the
Delta in coordination with the
federal Central Valley Project, and
the enhancement of fisheries and
wildlife habitat.
Construction was initiated in 1957
through special legislative appro-
priations following the disastrous
December 1955 flood, but the prin-
cipal financial base for the
Project's implementation was provided
in i960 by the citizens of California
through their approval of the Cal-
ifornia Water Resources Development
Bond Act, commonly referred to as
the Burns-Porter Act.
Features of the State Water Project
are shown on Figure 38. The Project
is described in detail in Department
of Water Resources Bulletin No. 132-70,
"The State Water Project in 1970",
and is described and illustrated in
digest form in Appendix C to that
bulletin. Upon completion, the
major physical facilities of the
State Water Project will include
21 dams, 6 hydroelectic powerplants
-148-
FIGURE 38
STATE OF CALIFORNIA
THE RESOURCES AGENCY
DEPARTMENT OF WATER RESOURCES
MAJOR FEATURES OF THE
STATE WATER PROJECT
AND THE
CENTRAL VALLEY PROJECT
LEGEND
■■ STATE WATER PROJECT
EIH CENTRAL VALLEY PROJECT
^Z3 JOINT USE FACILITIES
/Vorf/} Bay Aqueduct
SAN FRANCISCO
South Say Aqueduct-
and 22 pumping plants. The total
length of the conveyance systems
including canals, tunnels and
pipelines will be about 700 miles.
Current estimates indicate that
the total cost of the State Water
Project will be some $2.8 billion.
Upon full project deliveries the
State Water Project will supply
4,230,000 acre-feet annually to a
total of 31 water service agencies
which presently hold contracts with
the Department of Water Resources.
These agencies are located within
8 of the 11 hydrologic study areas
of California. These contracts
for project water by hydrologic
areas are as shown in the tabulation
at the bottom of this page.
In addition to the delivery of
maximum annual entitlements under
full project operation, the State
Water Project will also make deliv-
eries of water supplies for specific
recreational use on a nonreimburs-
able basis of approximately 45,000
acre-feet per year. This latter
supply plus diversions of approx-
imately 250,000 acre-feet per year
to offset operational losses, such
as seepage and evaporation, bring
the total present maximum State
Water Project diversion requirements
to 4,525,000 acre-feet per year.
Operational Characteristics
and Flexibilities
As the Central Valley Project and
State Water Project use common
stream channels and conveyance
facilities, and the water supplies
conserved and distributed become
physically indistinguishable, there
is a need for close coordination.
Such coordination also enables a
high degree of very desirable oper-
ational flexibility among the
facilities of the two-project
systems. Coordination of the op-
eration of the two projects will
become even more important in the
future as the Central Valley Basin
supplies become more fully utilized.
In recognition of this need, an
important operating agreement has
recently been negotiated between the
U. S. Bureau of Reclamation and the
California Department of Water
Resources. It is presently under
Hydrologic Area
Sacramento Basin
San Francisco Bay
Central Coastal
San Joaquin Basin
Tulare Basin
South Coastal
South Lahontan
Colorado Desert
TOTAL
5
5
2
1
7
5
5-
_3
31
3I/
2/
Maximum Annual Entitlement
(Acre-Feet Per Year)
39,800
255,000
82,700
5,700
1,349,300
2,204,400
214,600
78,500
4,230,000
1/ One agency in both South Coastal and Colorado Desert areas.
?/ One agency in both South Lahontan and Colorado Desert areas.
-150-
Portion of San Luis Joint-Use-Fycilities
Federal-State use involves close coordination
review by the Secretary of the
Interior. The agreement provides
the operators of the two projects
with the procedures necessary to
achieve the objectives set forth in
the various laws, orders, policies,
and other instruments under which
the Central Valley Project and State
Water Project are authorized to
operate. These procedures include
preparation of forecasts for pro-
posed operations, language for the
transfer or exchange of facilities
use, criteria for the allocation of
shortages, and procedures for
assigning the responsibility for
maintaining the objectives of the
operating agencies. While accom-
plishing the objectives of the
agreement, the separate identity of
facilities, resources, and contri-
butions of each project is
maintained.
Water Supply Capabilities
Current estimates by the Department
of Water Resources indicate that
the combined dependable water yield
for the "basic facilities" of the
Central Valley Project and the
State Water Project is on the order
of l4.4 million acre-feet annually.
"Basic facilities" are defined as
those facilities which are either
existing or under construction for
the federal Central Valley Project
and the "Initial facilities" of
the State Water Project as defined
in the Burns-Porter Act. The
principal basic facilities of the
two projects are listed in Table 9«
The indicated yield capacity of the
Central Valley Project-State Water
Project basic facilities is ref-
erenced to the 1990 time frame for
-151-
TABLV
q
MAJOR FEATURES
OF BASIC
CENTRAL VALLEY
PROJECT AND
STATE WATER PROJECT
SYSTEM
Central Valley Project
State Water Project
Major Reservoirs
Shasta
Oroville
Clair Engle (Trinity)
San Luis*
Whiskeytown
Pyramid
Auburn
Castaic
Folsom
Silverwcod (Cedar Springs)
San Luis*
Perris
New Me lone s
Millerton (Friant)
Major Canals
Corning
North Bay Aqueduct
Tehama -Colusa
Peripheral Canal*
Folsom South
South Bay Aqueduct
Peripheral Canal*
California Aqueduct, including
Contra Costa
Delta Mendota
joint San Luis Canal, Coastal
Branch and V/est Branch.
San Luis*
San Felipe Division
Friant-Kern
Friant-Madera
; Water
Proj
ect joint-use facilities.
* Central Valley Project-State
local upstream depletions within
the Sacramento River Basin. Pro-
jections are that by 2020 the
continuing development in these
upstream areas by local agencies
will reduce the 1990 level annual
yield of the combined federal-state
project system by about 200,000
acre feet.
The State considers its share of
this reduction as a commitment in
accordance with the "Delta Pooling
Concept". That concept, which is
premised on the counties of origin
and watershed protection statutes
of the California Water Code,
provides, in effect, that no water
shall be exported from an area in
which it originates, or from areas
immediately adjacent that can be
conveniently served by such water,
which is needed for the development
of those areas. Water supplies
may be depleted for upstream uses
in the counties of origin, and
local agencies in the area in and
above the Delta have a prior right
-152-
to contract for water service from
the State Water Project. These
principles are incorporated in the
contracts between the State and
the 31 water service contractors
for water deliveries from the State
Water Project.
Of the ik.H- million acre-foot
nominal yield for the 1990 time
period, approximately 3-9 million
acre-feet can be provided by the
initial conservation facilities of
the State Water Project and
10.5 million acre-feet by the
Central Valley Project. Correspond-
ing estimates taking into account
the 2020 level of upstream local
development are approximately 3-8
and 10.4 million acre-feet per
year, respectively.
These estimates of water supply
capability for the Central Valley
Project and State Water Project are
premised on a minimum Delta outflow
of 1,800 cubic feet per second.
This minimum outflow should not be
construed as representing the
average outflow which can be ex-
pected in a normal or above-normal
year. For example, estimates are
that under full 2020 development,
normal-year outflow would frequently
exceed 1,800 cubic feet per second.
As a comparison, 1,800 cubic feet
per second continuous outflow would
amount to I.3 million acre-feet per
year, whereas normal outflow to the
Bay under 2020 development would
average 7 million acre-feet per
year, or about five times the
minimum outflow.
The Role of the Peripheral Canal
The Peripheral Canal is an important
feature of the Central Valley
Project-State Water Project system.
The State has authority to construct
the Canal alone or by joint venture
under the 1959 Burns-Porter Act.
However, congressional authority is
needed for the Bureau of Reclamation
to participate in the Canal as part
of the federal Central Valley
Project.
The Peripheral Canal will not add
any new service 'sreas to the state
or federal projects nor will it
increase the authorized amount o'"
water slated for delivery by these
projects. The Canal simply solves
the water conveyance, water quality,
and fishery problems in the Delta
related to carrying water across
the Delta to the existing state
and federal conveyance facilities
and, at the same time, makes pos-
sible the redistribution of water
within the Delta itself.
Specifically the Canal would:
(1) protect and enhance the com-
mercial and sport fisheries and
other aquatic life that are
dependent upon the Delta by elim-
inating flow reversals and making
releases from the Canal; (2) avoid
using existing Delta channels as
conduits for conveyance of Project
water, thereby eliminating possible
channel scour and levee erosion
problems; (3) provide a firm supply
and improve water quality in the
interior Delta by redistributing
water through release facilities;
(4) provide salinity control in
the Delta in accordance with con-
ditions established by the State
Water Resources Control Board and
agreements with local interests;
and (5) fulfill the water transfer
and water quality requirements of
the State Water Project and the
federal Central Valley Project,
including the proposed Kellogg Unit,
or some similar project, to provide
water to the Contra Costa County
area.
The Peripheral Canal will consist
of a 43-mile-long unlined channel
that will skirt the easterly edge
of the Delta region. It will
originate at a diversion structure
on the Sacramento River near Hood,
and will terminate in the Clifton
Court Forebay at the southwesterly
portion of the Delta. Twelve
outlet structures will provide
freshwater releases at the crossings
of Delta channels in amounts
necessary to best control and improve
water quality in many interior
waterways .
-153-
The release works and the isolation
of water transfer from the existing
Delta channels will eliminate the
reverse flow problem during the
migration season for salmon, shad,
steelhead and striped bass. This,
in conjunction with adequate
waste discharge treatment, is ex-
pected to assist in a restoration
of San Joaquin River migratory
fish runs and enhance the Delta
fishery, particularly the striped
bass. The separate transfer
channel will also eliminate the
possibility of scour and levee
erosion in certain Delta channels,
and water level drawdown in south-
ern Delta channels. Salt water
intrusion from San Francisco Bay
can be better controlled by canal
releases .
Operation of the Peripheral Canal
will enable a very high degree of
flexibility. With its many release
gates and with control of pumping
rates, coordinated with upstream
reservoir releases, a wide variety
of flow and water quality patterns
could be provided within the Delta.
Recent operation studies conducted
by the Department indicate that
for water transportation purposes,
completion of the Peripheral Canal
should be scheduled not later than
1980. However, fish and game
interests want the Peripheral
Canal constructed as soon as
possible to prevent the further
deterioration of the Delta envi-
ronment and its fishery and to
provide for enhancement.
Projected Water Demands on
the Federal and State Systems
Upon completion of those facilities
of the Central Valley Project and
the State Water Project now under
construction, this federal-state
water resource development system
will be capable of providing water
services to all hydrologic areas of
California except the North Lahontan
area. Although no direct deliveries
for use within the North Coastal
area are anticipated from existing
facilities, the Trinity Division
of the Central Valley Project
possesses the potential to make
such deliveries if and when a
demand may occur.
Table 10 indicates the water
service anticipated to be supplied
from facilities of the two projects
new being completed and Table 11
shows the additional service which
could be provided from future
expansion of these projects.
Possible Central Valley
Project Expansion
An expansion of service under the
Central Valley Project by addition
of the planned major conveyance
facilities, namely the initial
East Side Division and the West
Sacramento Canals Unit, appears to
be the most favorable option for
meeting the bulk of the supple-
mental water demands anticipated
to occur within the Central Valley
Basin. Other areas of projected
deficiencies in dependable water
supplies in the Central Valley
could be served through addition
of the Cosumnes River Division and
the Allen Camp Unit, plus an ex-
tention of service under the
existing San Luis Unit. These
possible future additions to the
Central Valley Project are
illustrated on plate 1.
The East Side Division could provide
new and supplemental water service
to potential service areas along
the east side of the San Joaquin
Valley from the vicinity of
Stockton to Bakersfield. This
proposed extension could also pro-
vide beneficial services in the
categories of water quality control,
flood control, recreation, and
fishery and wildlife habitat en-
hancement. It is envisioned that
the Initial Phase would serve
1,500,000 acre-feet annually to
Fresno, Kings, Tulare and Kern
Counties. The water supply would
be derived from operation of ex-
isting storage facilities. Auburn
and New Melones Reservoirs which
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TABLE 10
SUMMARY OF I967 AND PROJECTED FUTURE WATER
DEMANDS ON EXISTING FACILITIES OF THE CENTRAL VALLEY PROJECT
AND STATE WATER PROJECT-
(1,000 Acre-Feet)
^^-- I
'• Central Valley Project- • State Water Project
Hydrologic Study Area . ^^^^ . ^g^^ . 5020 : 1967 : 1990 : 2020
San Francisco Bay 60 220
Central Coastal 0 80
South Coastal
Sacramento Basin 2,210 2,750
Delta-Central Sierra 98O 1,270 1.330
460
60
230
260
110
0
80
80
--
0
1,190
2.200
080
0
40
40
San Joaquin
1,580
1,670
1
,720
0
10
10
Tulare Basin
1,460
2,690
2
,690
0
1,350
1,350
South Lahontan
—
—
—
0
210
210
Colorado Desert
—
—
—
0
80
80
Recreation Deliveries
& Conveyance Losses
—
502^
50^/
--
290
290
Total Demands on
CVP £[nd SWP
6,290
8,730
9
,440
60
3.480
4,520
1/ Includes facilities under construction.
2/ Includes conveyance via project facilities of exchange
supplies in consideration of water rights.
3,/ Additional recreational deliveries and conveyance losses
for Central Valley Project are included in the study area values,
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TABLE 11
SUMMARY OF POSSIBLE FUTURE WATER DEMANDS ANTICIPATED
TO BE SUPPLIED BY FUTURE FACILITIES OF THE
CENTRAL VALLEY PROJECT AND STATE WATER PROJECT
(1,000 Acre-Feet)
• Central Valley Project— • State Water Project-
Hydrologic Study Area
1990
2020
1990
2020
San Francisco Bay
South Coastal
Sacramento Basin
Delta-Central Sierra
San Joaquin Basin
Tulare Basin
Colorado Desert
Conveyance Losses
—
—
30
300
—
—
0
130
210
310
—
--
90
160
—
--
300
590
~
--
1,170
1,840
0
250
200
200
Total Supplemental Demands
on CVP and SWP 1,970
3,100
0
250
0
ko
--
Uo
30
760
1/ Supplemental CVP facilities required to meet these demands include:
East Side Division, West Sacramento Canals Unit, Cosumnes River Unit,
Allen Camp Unit, and service extension within the existing San Luis
Unit, plus future conservation facilities yet unidentified.
2/ Supplemental SWP facilities required include parallel North Bay
and South Bay Aqueduct facilities, California Aqueduct modifications,
plus future conservation facilities yet unidentified.
are presently under construction,
and the offstream storage features
to be associated with the East Side
Division. This surface water sup-
ply could offset the present annual
ground water overdraft (in excess
of 1,000,000 acre-feet) and the
projected future increase in demand.
Physical features of the Initial
Phase include the East Side Canal,
five reservoirs, associated pumping
plants, and a distribution and
drainage system. The East Side
Canal, with source connections to
the Sacramento River by means of
the Hood-Clay connection, and to
the American River by means of the
authorized Folsom South Canal,
would extend 330 miles to its ter-
minus at the Kern River. Two of
the five reservoirs, Montgomery and
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Hungry Hollow, would serve as
major offstream storage facilities
with 986,000 acre-feet of combined
active storage.
Through provisions for stream
maintenance releases for fisheries,
recreation and water quality im-
provement purposes the East Side
Division would have the potential
for considerable environmental
enhancement of the Sierra-Nevada
streams from Dry Creek in Sacramento
County to the Kern River in Kern
County.
The West Sacramento Valley Canals
Unit could provide future water
service from the Central Valley
Project to the Yolo-Zamora, Lower
Cache Creek, and Solano service
areas in Yolo and Solano Counties.
Principal features would include
an enlarged portion of the Tehama-
Colusa Canal, presently under con-
struction; an extension of that
canal; and Sites Reservoir, a
1,200,000 acre-foot pumped-storage
reservoir. This new lake would be
located in western Colusa County
on lands which do not appear to
have significant recreational value
or high development potential. The
West Sacramento Canal could pro-
vide for an annual water conveyance
of 360,000 acre-feet, a portion of
which is developed by existing
Central Valley Project conservation
facilities, with the remainder to
be supplied through operation of
the Sites pumped-storage facility.
The Cosumnes River Division could
develop and convey 120,000 acre-
feet of water per year for irri-
gation and an additional 25,000
acre-feet annually for municipal
and industrial use, by means of
three reservoirs and an extensive
distribution system to service
areas in the foothill regions of
Sacramento, El Dorado, Amador and
San Joaquin Counties. The main
storage feature of the Cosumnes
River Division would be the
900,000-acre-foot Nashville Reser-
voir. Recreation facilities would
be provided at the reservoirs, and
flood protection would be provided
for floodplain lands now subject
to overflow. The meager fishery
resources of the lower Cosumnes
River system would be enhanced by
reservoir releases , and a new reser-
voir fishery W'.al'i be estribli shed .
The proposed Allen Camp Unit would
provide benefits to the Big Valley
area of Lassen and Modoc Counties
through irrigation, flood control,
fish and wildlife enhancement, and
recreation. Flows of the Pit River
would be controlled and conserved
by the proposed 190,000-acre-foot
Allen Camp Reservoir which could
provide a dependable annual yield
of 50,000 acre-feet. Diversions
would be made to irrigate 22,000
acres .
Possible State Water
Project Expansion
Current water demand studies by the
Department indicate that supplemental
water service from the State Water
Project may be desired within four
hydrologic study areas commencing
sometime after 1990. These are the
San Francisco Bay area, Tulare
Basin, and the Colorado Desert and
South Coastal areas. The term
"supplemental water service", as
used here, refers to the delivery
of water over and above the present
contract entitlements. The quan-
tities of potential supplemental
water service presently projected
to 2020 for these areas are listed
in Table 11.
San Francisco Bay Area. Within the
San Francisco Bay area possible
supplemental water demands from the
State Water Project could be on the
order of 30,000 acre-feet annually
by 1990 and 300,000 acre-feet an-
nually by 2020. Of this amount the
30,000 acre-feet in I99O and
170,000 acre-feet in 2020 would be
contingent upon location of an
industrial complex in the Collinsville
area of southern Solano County. The
additional 130,000 acre-feet of
anticipated supplemental demand by
2020 would develop in Santa Clara
County and the inland portions of
Alameda and Contra Costa Counties,
if recent growth trends continue.
-157-
Tulare Basin. Most of the fore-
casted supplemental water demands
within the Tulare Basin would be
located on the east side or within
areas contiguous to the present
federal San Luis Unit service area.
However, an additional 250,000 acre-
feet of annual supplemental water
service is estimated to be required
in western Kern County by 2020,
mostly in the Antelope Plain area
adjacent to present service areas
of the California Aqueduct. It is
assumed that the supplemental demand
in this area would be met by the
State Water Project.
Colorado Desert Area. A sizable
amount of urban growth is projected
for the Colorado Desert region
because of its proximity to Southern
California urban centers. Water
available from the State Water
Project could make possible the lo-
cation of new urban developments in
areas that are without water today.
Other urban areas may desire State
Project water because of its better
quality than from other available
sources .
Expanded State Water Project deliv-
eries to the Colorado Desert areas
would primarily serve increasing
municipal and industrial demands,
especially in Coachella Valley and
the uplands to the west and north
of that valley. Possible supple-
mental water service to accommodate
urban growth within the Colorado
Desert areas is assumed here to be
40,000 acre-feet annually by 2020.
South Coastal Area. The combined
dependable water supplies available
to the South Coastal area from ex-
isting sources, from facilities
under construction, and from waste
water reclamation projects now
definitely planned appear adequate
to meet water demands in this area
until after the turn of the century.
Projections are that by 2020 con-
tinued growth will require supple-
mental supplies on the
order of 650,000 acre-feet per year.
The shortage in supply is indicated
to begin by about 2010 (refer to
Figure 21 on page 108) .
Table 8 and the discussion in
Chapter VI identify three principal
options for meeting this projected
long-range demand for supplemental
supplies. These are: future
waste water reclamation in addition
to the 300,000 acre- feet per year
which is now definitely planned,
desalination of sea water, and sup-
plemental imports via the State
Water Project. Although these de-
mands may possibly be met from any
one of these supply options, they
will probably be met by a combination
of these sources.
The State Water
potential for p
service to the
as arrangements
Southern Califo
provide future
certain reaches
Aqueduct. This
about 190 cubic
Kettleman City
delivery equiva
feet.
Project has the
roviding expanded
South Coastal area,
have been made by
rnia contractors to
use capacity in
of the California
reserve capacity is
feet per second for
southward or an annual
lent of 130,000 acre-
For purposes of this analysis, this
reserve capacity is assumed to be
utilized and the State Water Project
is assumed to supply supplemental
water service of 130,000 acre-feet
annually to the South Coastal area
by 2020. The remainder of the
projected supply deficiency could
be met by waste water reclamation
and/or desalination. Future studies
by the Department and the concerned
water agencies may, of course, in-
dicate the desirability for either
greater or less future deliveries
from the State Water Project than
assumed here. Considerable addi-
tional study is needed; however,
ample time is available for such
study and for a determination by
the people concerned regarding the
most favorable course of action.
Central Valley Project Water
Demand-Supply Relationship
Figure 39 illustrates the water
demand-supply time relationship for
the Central Valley Project with the
East Side Division, West Sacramento
-158-
Canals Unit, Cosumnes River Division,
and the Allen Camp Unit added. The
solid blue line indicates the water
supplies that could be made avail-
able by the expanded Central Valley
Project, incorporating those facil-
ities. The broken blue line
indicates the dependable water
supplies developed by present proj-
ect facilities, including both
those completed and under construc-
tion. The solid and broken red
lines represent the demand on the
expanded project and the present
project, respectively.
The figure illustrates that suffi-
cient supplies are presently
developed under the Central Valley
Project (broken blue line) to
accommodate a considerable expansion
in future service without a require-
ment for additional conservation
features. However, a requirement
exists for construction of major
conveyance facilities, namely the
East Side Division and West
Sacramento Canal, to serve areas
of present and incipient defi-
ciencies in the Tulare and Sacramento
Basins .
Figure 39 further illustrates that
additional conservation facilities
(exclusive of those identified in
that figure) may not be required
under the Central Valley Project
for water supply purposes alone
until about 2000. The figure
also indicates that by 2020 the
possible expanded service could
require additional water conser-
vation features to provide new and
supplemental supplies on the order
of 1 million acre-feet annually.
These additional features are not
presently identified. They may
include the full spectrum of the
potential supply options which
were discussed in Chapter V.
State Water Project Water
Demand-Supply Relationship
Figure 4o illustrates graphically
the current assessment by the
Department of Water Resources of
the rate of buildup in water demand
from the State Water Project and
the water supplies available from
the initial conservation facilities.
The blue line indicates the de-
pendable water yield capability of
the initial conservation facilities.
The solid red line shows the proj-
ected total buildup in water
demands, and the broken red line
indicates the demand buildup under
the present water service contracts,
as estimated by the Department as
a result of a review with the water
supply contractors.
Figure kO indicates
tional conservation
first be needed in
on the basis of the
mated rate of build
deliveries under pr
This represents a d
10 years from the p
of need for an addi
as published in Bui
that an addi-
facility would
the mid-1990s
currently esti-
up for water
esent contracts,
elay of some
rojected timing
tional facility
letin 160-66.
Figure ^ also shows that on the
basis of projected total demand
from the State Water Project, ex-
panded conservation facilities may
also be needed commencing in the
mid-1990s, and that these facilities
might need to provide a further
dependable annual water supply of
about 700,000 acre-feet by 2020, in
addition to the existing contract
entitlements .
It should be emphasized that the
forecast of timing of need for
additional water is premised upon
assumptions regarding future events
which cannot now be foreseen. For
example, the Department of Water
Resources believes that the commit-
ments to provide good quality water
in the Delta can be met by a mini-
mum Delta outflow of 1,800 cubic
feet per second. Should a decision
by the State Water Resources Control
Board impose conditions which might
require greater releases than
l.oOO cubic feet per second, the
timing of need for additional
water would be advanced.
-159-
FIGURE 39
THE CENTRAL VALLEY
PROJECT
PROJECTED NET WATER DEMANDS
AND
DEPENDABLE WATER SUPPLIES
14,-
10
UJ
o
< 6
PROJECTED DEMANDS
PROJECTED SUPPLIES
SUPPLIES FROM
EXISTING
FACILITIES
1970
DEMANDS ON
'existing FACILITIES
1980
1990 2000
YEAR
2010
2020
Figure 40
THE STATE WATER PROJECT
PROJECTED NET WATER DEMANDS
AND
DEPENDABLE WATER SUPPLIES
6r
PROJECTED DEMANDS
SUPPLIES FROM
EXISTING
FACILITIES
EXISTING CONTRACTUAL-
COMMITMENTS
DEMANDS UNDER
EXISTING CONTRACTS
ADDITIONAL
SUPPLIES
REQUIRED
1970
1980
1990
2000
2010
2020
YEAR
Other factors that would accelerate
the need for additional water are:
(l) problems of quality of Colorado
River Water which might necessitate
substitution of water from the State
Water Project; (2) more rapid pop-
ulation increase than presently
anticipated; (3) a demand for proj-
ect water in service areas not now
under contract; and (4) Increased
water use in areas tributary to the
Delta.
Factors that would tend to delay
additional need for water are:
(l) a slower population growth than
now anticipated; (2) more rapid
development in technology of de-
salting than now anticipated; and
(3) a greater reuse of reclaimed
water than now projected. A
continuing evaluation of all these
factors will be necessary to effect
the overall most acceptable means
of satisfying future demands.
The Department of Water Resources
is presently conducting studies of
the various options for meeting its
commitments to water contractors
under the State Water Project and
for supplying the future supple-
mental service which may be requested.
Because of the slowdown in demand
Increase in relation to earlier
estimates and the Indicated delay
in timing of need for additional
facilities, the Department will
have sufficient time available to
study and analyze alternative
sources with full consideration of
environmental factors.
-I6l-
Recreational and Environmental
Accomplishments
The water demands and the supply
capabilities of the Central Valley-
Project and State Water Project
have been presented In some detail
to demonstrate their abilities to
fulfill obligations to the water
supply contractors and to meet
probable future supplemental water
demands. In addition to meeting
these obligations, however, the
multi-purpose facilities of the
Central Valley Project and the
State Water Project have made pos-
sible an array of other Important
services. These include: flood
control, hydroelectric power pro-
duction, water quality control,
water-oriented recreation oppor-
tunities, and the improvement of
fisheries and wildlife habitat.
Each of these services is Indeed
a water resource management purpose
in its own right. In most instances
these services could not have been
economically provided except through
the advantages Inherent in the
multi-purpose management concept.
Contributions of the two projects
in providing these services have
substantially enhanced California's
natural human environment. Flood
control has eliminated the threat
of damage to the lives and property
of many of the State's citizens;
hydroelectric power production
provides a significant portion of
the electric energy needed without
pollution of the atmosphere or the
water supplies; and water quality
control provides for the availabil-
ity of dry-period streamflows in
many of California's rivers and
estuaries for salinity repulsion
and other purposes that were not
available under natural or
pre-project conditions.
The increase in population and the
general movement from rural to
highly urbanized areas have devel-
oped an unprecedented demand for
water-oriented recreation and other
experiences related to enjoyment of
the environment. The following
sections briefly describe what the
State Water Project and the Central
Valley Project are doing toward
providing for the recreational and
environmental needs, including flood
control, of the people of California,
Environment and the
Central Valley Project
Recreation has long been recognized
by the Bureau of Reclamation as one
of the benefits to be derived from
the creation of new lakes. To
enhance the public enjoyment these
large bodies of water have been
provided with campgrounds, picnic
areas, piped water, sanitary facil-
ities, riding and hiking trails,
beaches, boat-launching ramps, and
boat docks. As the need is dem-
onstrated these facilities are
improved and expanded. The major
structures of the project are
themselves an attraction to sight-
seers, and many visitors stop each
year at the visitor facilities to
view the dams, powerplants . and
related facilities.
The project lakes are stocked with
fish, and in many cases the fishing
in streams below the dams Is en-
hanced by maintenance of more stable
flows, either specifically for fish
enhancement or as a result of other
project flow requirements. The
operation of Shasta Reservoir and
the Coleman Fish Hatchery has been
largely responsible for the enhance-
ment of the valuable steelhead
trout fishery on the Sacramento
River. Three fish hatcheries are
operating to replace spawning areas
cut off by dams on the Trinity,
Sacramento, and American Rivers.
Central Valley Project reservoirs are
also used by waterfowl for nesting
and for resting during migration.
It is estimated that in I969 there
were about 1,130,000 use-days by
ducks and geese on project water
areas. Hunters took about 3^,000
waterfowl during the hunting season.
In addition, for a number of years
the project has supplied supple-
mental water for the State's
Mendota Waterfowl Management area
in the San Joaquin Valley.
-162-
Two facilities of the Central
Valley Project now under construc-
tion. Auburn and New Melones
Reservoirs, will contribute ben-
efits from further recreation,
fisheries and wildlife enhancement.
In addition to the new lake areas
for fishing and recreation, these
deep reservoirs will supply water
at temperatures lower than presently
available for releases to maintain
downstream trout and salmon fish-
eries. Also, the operation of
Auburn Reservoir in conjunction
with Lake Folsom will enhance the
already high-quality recreation
provided by the latter through a
reduction in water level fluctu-
ations and the maintenance of
generally higher storage levels.
Located adjacent to the Sacramento
metropolitan area. Lake Folsom has
been the most popular of the project
reservoirs. In 19^9 more than
2.U million visitor-days were re-
corded. Second in use was Lake
Shasta, the largest of the project
reservoirs, with more than 1.7 mil-
lion visitor-days of recreation
use .
The overall Central Valley Project
provided a total recreation-use in
1969 of about 6.5 million visitor-
days, as shown by project facility
in Table 12.
The regulation of streamflow
extremes is another significant
environmental benefit inherent in
the operation of the Central Valley
Project conservation facilities.
The catastrophic floods of 1964,
which caused record damage in the
North Coastal area, also produced
new record peak runoff in the
Central Valley Basin. In the latter
area, however, operation of flood
control facilities prevented exten-
sive damage. On the American River,
for example, the December 1964 peak
inflow to Lake Folsom was 280,000
cubic feet per second. Downstream
releases were limited by the oper-
ation of Lake Folsom to 115,000 cubic
feet per second, the design capacity
of the channel. Without Folsom Dam
and Reservoir, the Sacramento
metropolitan area would have been
flooded.
During the storm of January 1970,
Lake Shasta experienced its greatest
peak inflow of record--210 ,000 cubic
feet per second. Downstream re-
leases were held to a maximum of
15,000 cubic feet per second at the
time of peak inflow into the lake
and were increased to a maximum of
only 79,000 cubic feet per second,
subsequently, during that storm
period, thus minimizing overflow
damage in the Sacramento Valley.
Lake Shasta has regulated five such
major flood flows since its
completion in 1944.
Finally, mention should be made of
improvement to salinity conditions
in the Delta since Shasta Dam com-
menced operation in 1944. During
the 25 years prior to construction
of Shasta Dam there were seven years
of severe salinity intrusion into
the interior Delta channels, and in
1931 salinity from the ocean in-
truded upstream beyond the City of
Stockton. Since 1944 water released
through operation of Shasta Reservoir
has prevented serious intrusion of
saline water into interior Delta
channels. Had no releases from
storage been made, salt water would
have advanced well into the interior
of the Delta in 7 of the 10 years
from 1955 through 1964. The State
Water Project will share responsi-
bility for, and maintenance of,
water quality in the Delta.
Environment and the
State Water Project
Completed facilities of the State
Water Project have already seen
intensive use by recreationists.
The three Upper Feather area reser-
voirs (Frenchman, Antelope, and
Lake Davis), designed primarily for
recreational purposes, were among
the first units completed and have
supported an increasing use, with
933,000 recreation-days recorded in
1969. These projects are providing
new lake habitat for fish, water-
based sports opportunities, onshore
-163-
camping and picnic areas, mainte-
nance of downstream summer flow for
fish, and general improvement of
the streamshore environment.
Downstream on the Feather River,
Lake Oroville became available for
recreation-use in I968; and the
Oroville complex, including
Thermalito Forebay and Afterbay,
supported 517,^00 recreation-days
of use in 1969- In addition to the
usual boating, fishing, and onshore
recreational activities at Lake
Oroville and Thermalito Forebay,
the Afterbay, with 4,500 surface
acres, offers waterfowl hunting.
Besides the waterfowl habitat pro-
vided by the reservoirs, the
5,700-acre Oroville Borrow area
will be developed for waterfowl
and upland game habitat and for
warmwater fishing in the numerous
sloughs and ponds.
The Sacramento-San Joaquin Delta
perhaps has received more attention
than any other area in the study of
the effects of proposed water
control facilities on the preser-
vation and enhancement of the
aquatic environment. Consideration
of fish and wildlife ecological
requirements had much to do with
the choice of the Peripheral Canal
as the Delta facility for the State
Water Project. The canal was pro-
posed by a joint interagency com-
mittee as the best means of
conveying water to the pumps of the
U. S. Bureau of Reclamation Delta
Mendota Canal at Tracy and the Delta
Pumping Plant of the California
Auqeduct, while at the same time
providing for controlled releases
into the Delta channels for salinity
repulsion, maintenance of a balanced
ecology in the Delta necessary for
preservation and improvement of
sports and commercial fisheries,
and improvement of the general Delta
environment as it relates to agri-
culture and recreation use. More
than $9 million has been invested
by the state agencies in planning
and investigation related to rec-
reation and fish and wildlife
protection and enhancement in
the Delta.
On the South Bay Aqueduct, in
Alameda County, Del Valle Dam has
been completed adjacent to the San
Francisco Bay metropolitan area.
The reservoir replaces a stream of
intermittent flow with no fishery.
It has been stocked with fish by
the Department of Fish and Game and
onshore facilities have been pro-
vided by the Department of Parks
and Recreation for the many nearby
residents who are this year begin-
ning to enjoy the many recreational
activities offered by this stra-
tegically located body of water.
Further south along the California
Aqueduct, San Luis Reservoir.
O'Neill Forebay, and Los Banos
Reservoir present an opportunity
for water-based recreation in an
area historically void of signif-
icant bodies of water. Initial
facilities for recreationists have
been constructed at O'Neill Forebay
which has had the heaviest use;
however, facilities at three areas
on the shore of San Luis Reservoir
are now available and are coming
into increasing use. Waterfowl
shooting is also available at all
three reservoirs.
The 280-mile completed section of
the California Aqueduct in the
San Joaquin Valley already possesses
a sizable fish population, chiefly
catfish and bass. Four fishing
access sites have recently been
constructed along the aqueduct by
the Wildlife Conservation Board
and opened to public use. More
will he constructed as the demand
develops .
South of the Tehachapi Mountains in
Southern California, three
reservoirs--Pyramid, Castaic and
Silverwood--are under construction
and Perris will soon be underway.
They will help meet the demand in
that heavily populated area for
recreational experiences associated
with large bodies of water. Plans
for stocking of fish and for shore
developments are progressing and
will be implemented to provide
access to and use of the reservoirs
when they become operational. Also
-164-
TABLE 12
CENTRAL VALLEY PROJECT
RECREATION-USE IN I969
Feature Recreation -Days
Clair Engle Lake(Trlnlty ) 148,000
Lewlston Lake 45,000
Whiskeytown Lake 1,044,000
Shasta Lake 1,717,000
Keswick Reservoir 5,000
Jenkinson Lake (Sly Park) 223,000
Folsom Lake 2,405,000
Lake Natoira (Nimbus) 370,000
Mlllerton Lake (Priant) 366,000
Lake Woollomes 108,000
San Luis Reservoir *
O'Neill Forebay *
Los Banos Reservoir *
San Luis Wasteway 12,000
Contra Loma Reservoir 58,000
Red Bluff Diversion Dam 4,000
Delta Mendota Canal Angling Access Sites 25,000
TOTAL 6,530,000
•Federal -state Joint-use features reported under State Water
Project in Table 13.
-165-
O. 3872-5
One ot lour fishing access sites constructed along the Calilomia Aqueduct
under investigation is the develop-
ment of wildlife habitat within
the aqueduct right-of-way, partic-
ularly in the San Joaquin Valley
and in the Antelope Valley-Mojave
area.
Table 13 presents recorded
recreational use of State Water
Project facilities in 1969 and
estimated use under full develop-
ment for those units presently
shceduled for construction. Addi-
tional developments such as aquatic
recreation areas and ecological
areas in connection with the Project
facilities are under consideration
for inclusion as the demand develops
and as funding becomes available.
The State Water Project made its
first major contribution in the
interest of flood control during
the period of the extensive I964
flood. Oroville Dam, although only
partially completed, received a
maximum record peak inflow of
253,000 cubic feet per second and
impounded 155,000 acre-feet of
water during the storm period. The
reduction of the peak flow to
158,000 cubic feet per second out-
flow from the reservoir is estimated
to have prevented $30 million in
damages in the Yuba City-Marysville
area.
Summary
This chapter has described the roles
of the Central Valley Project and
the State Water Project in the
management of California's water
resources. It has indicated the
present services provided by these
projects, the coordination aspects
of their operation, and their
-166-
TABLE 13
RECREATION-USE AT STATE WATER PROJECT FACILITIES
(in recreation -days)
Feature
Antelope Lake
Lake Davis
Frenchman Lake
Lake Orovllle and Thermalito
Porebay and Afterbay
Peripheral Canal
Bethany Reservoir
Lake Del Valle
San Luis Reservoir, O'Neill
Porebay, and Los Banos Reservoir
Silverwood Lake
Lake Perris
Pyramid Lake
Castaic Lake
Aqueduct Angling Access Sites
Frenchman Flat-Piru Creek Fishery
Enhancement
TOTAL
Annual Recreation Use
1969
99,300
439,300
394,500
516,400
105,300
: Estimated Under
: Pull Development
1,554,800
301,000
476,000
474,000
6,213,000
2,500,000
50,000
3,370,000
4,483, OOoi-'"'^
2,188,000
5,346,000
70,000
2,500,000
2/
320,000
28,291,000
1/ Federal -state Joint-use facilities. ,-,-,,,
2/ Four sites were opened in late 1969 and 1970. More sites will be
opened as the demand develops.
-157-
potential for providing future
services to the people of
California.
The chapter has identified and
discussed the need for certain
priority additions to the convey-
ance facilities of the two projects
Those additions are the joint
federal-state Peripheral Canal and
the East Side Division and West
Sacramento Canals Unit of the
Central Valley Project, Other
proposed Central Valley Project
extensions discussed, for which an
incipient demand is forecast, are
the Cosumnes River Division and
the Allen Camp Unit.
The text and
Chapter VII
will be a ne
servation fa
Central Vail
State Water
these latter
be required
poses as ear
illustrations in
indicate that there
ed for future con-
cilities for both the
ey Project and the
Project, but that
facilities may not
for water supply pur-
ly in time as previous
estimates had shown. This possible
deferral in the need for the addi-
tional conservation facilities
results primarily from the slower
growth rates in population,
industry and agriculture which are
now projected for California.
No attempt has been made to identify
or recommend, from among the array
of potential source options (as
discussed in Chapter V), those
future water conservation measures
or facilities which may be reauired
after the mid-1990s. It is pres-
ently believed that ample study
time is available before specific
recommendations must be made and
that ample review time is like-
wise available for public
consideration of those recommendations.
The chapter concluded with brief
discussions of the environmental
accomplishments of the Central
Valley Project and the State Water
Project with emphasis on the
recreational opportunities afforded.
-168-
CHAPTER VIII, POPULATION DISPERSAL-
IMPACT ON RESOURCES DEVELOPMENT
The population projections discussed
in Chapter IV are based upon recent
population trends. Generally these
trends indicate the continued rapid
growth of existing urban areas. The
purpose of this chapter is to ex-
plore an approach based on possible
alternative land use policies
involving a redistribution of people
and estimate the impact of these
policies on water management. Time
limitations have precluded an in-
depth evaluation. As Indicated in
Chapter III, a thorough systems
analysis is required to define the
impacts and consequences of such land
use policy alternatives. However,
it has been possible to explore on
a superficial basis, at least, some
of the pertinent ramifications.
Considerable concern has been
expressed by legislative and public
groups that a continuation of the
growth pattern may have serious
social and environmental conse-
quences. It is argued that existing
metropolitan areas, particularly the
South Coast, already are overcrowded
and that the resultant environmental
problems, such as urban congestion
and air pollution, are so serious
that a further population increase
should not occur. Some proponents
of land use and urban population
control advocate control of popu-
lation in Southern California by
halting construction of the State
Water Project. Others express the
belief that the people should move
to the northern areas of water sur-
plus to avoid the necessity of
sending more water to the south.
The need for land use and population
policy has been widely discussed.
This need is closely related to the
view that resources development
planning should take into account
the total environment. Both the
Federal Government and the State are
taking steps leading toward defini-
tion and implementation of such policy.
At the federal level, legislation is
being considered which calls for a
National Land Use Council responsi-
ble for general land use policies.
In addition, under the new communi-
ties provisions of Title IV of the
Housing and Urban Development Act
of 1968, the Department of Housing
and Urban Development can guarantee
debt to a maximum of $50 million on
a single new town or new community
project .
Chapter II mentioned that two impor-
tant measures were passed by the
State Legislature in 1970. '^ The
first, AB 2045, required all state
agencies, boards, and commissions
to include In any report on any
public program which could have a
significant effect on the environ-
ment of the State a detailed state-
ment setting forth specified infor-
mation concerning the Impact on the
environment. The second, AB 2070,
established a comprehensive state
planning function in the Office of
the Governor known as the State
Office of Planning and Research.
This Office will be responsible for
the development of long-range state-
wide goals and policies for land
use, population growth and distri-
bution, open space and other factors
influencing quality of the State's
environment. One of the first tasks
will be to provide an analysis of
alternative approaches to accommo-
dating future population growth and
urbanization within the State. The
study will examine the probable
consequences of continuing to
accommodate future population within
existing metropolitan and urban
areas and will assess the physical,
social and economic Impacts which
would result if a substantial num-
ber of people were located in areas
where urbanization is not now
anticipated. The Department of
Water Resources is assisting in the
land use and population policy
study.
-169-
f Highways
Concern has been expressed that a continuation of present urban growth patterns may have serious
social and environmental consequences
The remainder of this chapter dis-
cusses the possible impact of three
hypothetical alternative patterns
of population distribution on water
development, use and disposal. It
also briefly discusses related con-
siderations of electric power,
transportation and air pollution.
These three population distribution
patterns, or models, are premised
on the projected statewide total
population of 45 million in 2020
described in some detail in
Chapter IV, but with different geo-
graphical locations and densities.
The distribution based on historical
trends is included as a "base" pro-
jection to facilitate a more valid
comparison of the impacts of these
three models.
Study Criteria
As a first step in selecting hypo-
thetical areas of future urbaniza-
tion for study, the Department of
Water Resources updated its mapped
information on all lands presently
irrigated and capable of irrigation
(see Plate 2). The study was prem-
ised on the preservation of irri-
gable lands for agricultural pur-
poses, and the identification of
large blocks of land in both public
and private ownership throughout
the State which would be physically
capable of accommodating urban
development while avoiding agricul-
tural lands. Other criteria for
selecting these lands were that:
lands have a slope no greater than
30 percent; urbanization would not
result in the loss of lands with
Important value for resources manage-
ment; weight be given to those
lands that were (l) located in the
coastal environment, (2) located in
close relation to recreation
resources (mountains, foothills,
forests, reservoirs, desert areas,
etc.), and (3) accessible by exist-
ing transportation facilities.
While the majority of land areas
selected for analysis are in private
-170-
ownership, some of the areas are
within the public domain, adminis-
tered by the Bureau of Land Manage-
ment. Public lands in National
Forests, national parks, wildlife
refuges, and Indian and military-
reservations were excluded from
consideration.
A basic assumption underlying the
selection process was that the
economic conditions required to
support urbanization would exist.
It was also assumed that different
combinations of land areas would be
capable of accommodating approxi-
mately 50 percent of the 25.2 million
anticipated population growth dur-
ing the period from 1970 to 2020.
This would involve 12.6 million
people. The remaining 12.6 million
people were considered to be located
within existing but expanded areas
of metropolitan and urban
development .
Three models for population distri-
bution were developed within the
context of the foregoing criteria
and assumptions. Model "A" empha-
sizes a greater allocation of
population to the northern portion
of the State, Model "B" is oriented
to the central portion, and
Model "C" to the southern portion
of the State. Figure 4l depicts
the distribution of the total popu-
lation in 2020 by hydrologic areas.
Figure 42 illustrates the distribu-
tion of people for each of the
three models.
The primary focus in the develop-
ment of the three hypothetical
population distribution models was
to provide a basis for evaluation
of the impact upon the California
water development program. It
should be emphasized that the
assumptions and parameters placed
upon the study are very general
and broad, and that tHe models
should not be Interpreted as
recommended development policies .
The models were selected to provide
a diverse set of options for review.
The northern model (Model "A")
emphasizes the area from the Delta
north to the Oregon border and
reflects essentially a pattern of
statewide development which would
bring a far greater number of people
to the primary sources of water.
Approxim.ately 50 percent of the
12.6 million distributed population
would go to the northern area.
Excepting the San Francisco Bay,
Stockton and Sacramento areas, most
of the distribution would be in the
upper Sacramento Valley and adja-
cent foothill areas of the Coast
Range and Sierra Nevada. The
remaining 50 percent would be
distributed to the central and
southern areas of the State in
roughly the same portions as would
be expected by a continuation of
current growth trends in these
areas .
The central model (Model "b" )
emphasizes the area between the
Delta and the Tehachapi Mountain
Range in Kern County. Most of the
distributed population would be
allocated to the Santa Cruz-Monterey
and San Luis Obispo-Point Conception
areas of the Central Coast, and to
the Sierra Nevada foothill areas in
Fresno, Madera, Mariposa, Merced,
Stanislaus and Tuolumne Counties.
Lesser allocations were made to the
eastern slope of the Coast Range
along the west side of the San
Joaquin Valley.
The southern model (Model "C")
emphasizes the area between the
Tehachapis and the Mexican border
and reflects in large degree a con-
tinuation of current trends in
population growth within the
Southern California region as a
whole . However, the model directs
substantial population to essen-
tially nonurban desert areas and
to South Coastal areas between San
Diego and San Clemente. Desert
areas involve primarily lands in
the public domain in the Palm Desert
and in the vicinity of Blythe in the
Mojave Desert. Lesser concentratiors
of urbanization are also shown in
the foothills bordering the
Antelope Valley.
The selection of areas for each of
the three models was somewhat
arbitrary, as there are other lands
-171-
FIGURE 41
2020 POPULATION FOR BASE PROJECTION
AND POPULATION DISPERSAL FOR
MODELS A, B AND C
HYDROLOGIC STUDY AREAS
NORTH COASTAL
SAN FRANCISCO BAY
CENTRAL COASTAL
SOUTH COASTAL
SACRAMENTO BASIN
DELTA- CENTRAL SIERRA
SAN JOAQUIN BASIN
TULARE BASIN
NORTH LAHONTAN
SOUTH LAHONTAN
COLORADO DESERT
LEGEND
E
Q-
1
B
C
Z
O 5 -
_i
1
■
^
■
* POPULATION DISTRIBUTION BASED ON HISTORICAL TRENDS
• *SEE DEFINITION IN TEXT.
-172-
FIGURE 42
POPULATION DISPERSAL TO NEW URBAN AREAS
FOR MODELS A, B AND C
HYDROLOGIC STUDY AREAS
NC - NORTH COASTAL
SAN FRANCISCO BAY
CENTRAL COASTAL
SOUTH COASTAL
SACRAMENTO BASIN
DELTA- CENTRAL SIERRA
SAN JOAQUIN BASIN
TULARE BASIN
NORTH LAHONTAN
SOUTH LAHONTAN
COLORADO DESERT
-173-
that meet the criteria and assump-
tions described. The amount of
land utilized in each of the models
is capable of accommodating the
number of people allocated to the
area, based on the assumption that
future development in new areas
would occur at roughly the same
densities of development as exist
in currently developed areas.
Impact of Population Dispersal
on Water Development
and the Environment
In considering the impact of the
population dispersal models upon
long-range planning and development
of the State, particular considera-
tion was given to the impact on
water demands. Other aspects such
as waste disposal, electric power
requirements, transportation and
air pollution are only touched upon,
recognizing that more intensive
planning and study would be required
for an adequate assessment.
Water Demand and Supply
The three hypothetical population
distribution models Illustrate the
consequences of a range of disper-
sions of future population growth
with regard to water demands. The
projected water demands in 2020 for
the "base" projection and each of
the three models are shown in
Table 14.
The water development facilities
presently existing and under con-
struction by federal, state and
local agencies throughout Califor-
nia have the physical potential
and flexibility to accommodate a
wide range of alternative future
patterns of population growth and
dispersal. Technological advance-
ment in such areas as desalting and
water reclamation further increase
this potential and flexibility.
Chapter VI provides information and
estimates on the dependable water
supplies which could be provided by
these developments.
TABLE 14
NET URBAN WATER DEMANDS IN 2020
FOR SELECTED ALTERNATIVE PATTERNS OP FUTURE URBANIZATION
(1,000 acre-feet)
Hydrologic
Study Area
North Coastal
San Francisco Bay
Central Coastal
South Coastal
Sacramento Basin
Delta-Central Sierra
San Joaquin Basin
Tulare Basin
North Lahontan
South Lahontan
Colorado Desert
State Total
Base
210
2,480
470
4,920
880
460
140
250
130
200
160
10,300
Population Models
250
1,690
1,050
3,480
2,510
830
320
190
230
340
160
11,050
B
210
1,690
1,770
3,310
1,080
430
560
280
130
450
160
10,070
250
1,690
820
3,830
1,080
390
140
190
130
550
1,350
10,420
-174-
Table 1^ shows that the three popu-
lation dispersal models reflect a
lesser population increase and
resultant slower buildup in net
urban water demands within the San
Francisco Bay and South Coastal
hydrologic study areas than would
occur under the "base" projection.
However, there is essentially
either the same or a greater future
net urban water demand in each of
the other study areas. It is also
interesting to note that the total
statewide water demand in 2020 is
greater under P'^odel "A" than under
the "base" projection, and that
demands are essentially the same
under Models "b" and "C" as under
the "base" projection. The higher
water demand under Model "A"
reflects the impact of dispersing
people to inland areas where per
capita water use is generally
greatest.
The following paragraphs provide a
very general discussion of the
potential for supply exchanges in
connection with existing develop-
ment and the additional water
supply measures and options indi-
cated by the population growth
patterns envisioned by the three
models. It must be recognized that
numerous legal and administration
issues would need resolution to
carry out some exchanges.
Northern Model "A". The resultant
increase in anticipated urban water
demands in the North Coastal region
could be met by local streams
development along the Mendocino
Coast. In the Central Coastal
region, future demands around
Monterey Bay could be met from
reserve supplies from the South San
Francisco Bay area (water which
would not be needed with a shift of
future population increase); and
similar demands in the southern
portion of the region could be off-
set by transfers of reserve supplies
from the South Coastal area.
Water demands for the new urban
center in the upper Sacramento
Basin could be provided by reserves,
local streams development or by
importation from the North Coastal
area. Additional demands in the
Delta-Central Sierra area could be
supplied in part from American and
Cosumnes Rivers sources with addi-
tional supplies obtained from
reserves available to the San
Francisco Bay area or by other im-
ports from the Sacramento Basin.
New cities in the Sierra foothills
and other new demands in the San
Joaquin Basin could be served from
the Friant Unit and the proposed
East Side Division of the Central
Valley Proj'ect. New urban develop-
ments on the east and west sides of
the Tulare Basin could be served,
respectively, by the East Side
Division and by diversions of water
supplies from the California Aque-
duct that would not be needed in the
South Coastal area under this popu-
lation distribution alternative.
Additional demands in the North
Lahontan area could only partially
be met by developing local streams
and probably would require imports
from the Sacramento Basin.
The projected additional urban water
demands in the South Lahontan area
could be supplied by diversions of
water supplies from Los Angeles
Aqueduct or the California Aqueduct
that would not be needed in the
South Coastal region under conditions
imposed for this population model
study. The Colorado Desert could
similarly be served by diversions
from the Colorado Aqueduct.
Central Model "B" . Under this cen-
tral-oriented model major new popu-
lation centers are envisioned along
the Central Coastal areas of Monterey
Bay and the Santa Maria and Santa
Ynez Valleys. New cities are also
envisioned along the Sierra foothills
in the San Joaquin Basin. As in the
other models, the population increase
in the San Francisco Bay and South
Coastal areas would be less than
anticipated under the "base" pro-
jection. The much larger demands in
the Central Coastal area could be
satisfied by a transfer of reserve
supplies from the San Francisco Bay
and South Coastal areas, coupled
-175-
with local streams developments and
by the desalting of sea water.
Also, water reclamation could assist
in extending the water supply. The
additional Model "B" urban water
demands in the Sacramento Basin
could be supplied from reserves ;
and those in the Delta-Central
Sierra could be met from American
River sources. For the most part,
the new communities along the east
side of the San Joaquin Basin could
be supplied by the proposed East
Side Division of the Central Valley
Project. The new cities on the
east side of the Tulare Basin could
also be served by the East Side
Division, and the California Aque-
duct could provide the necessary
water supplies for those cities on
the west side of the Basin. Demands
in the North Lahontan area could be
met by the development of local
streams. Supplies for the new
urban centers in the South Lahontan
and Colorado Desert areas could be
provided by diversions of water
from the Los Angeles and Colorado
Aqueducts that would not be needed
in the South Coastal area under the
assumptions of this population
model .
Southern Model "C". For the
southern-oriented population model
the largest new cities are suggested
in the South Lahontan and Colorado
Desert areas. New cities in the
desert region would require an
Importation of more water from
greater distances than in the other
models .
The large new cities suggested in
the Mojave area could be served by
increased deliveries via the
California Aqueduct. Extension of
the aqueduct could also serve por-
tions of the water demand created
by the suggested cities in the
Colorado Desert. Colorado River
water supplies presently allocated
to the South Coastal region could
also be used to meet part of the
needs in these new cities.
The additional urban demands sug-
gested by the southern-oriented
model in the North Coastal,
San Francisco Bay, South Coastal,
Sacramento Basin, Delta-Central
Sierra, Tulare Basin and North
Lahontan areas could be met by
essentially the same means as the
projected demands in the central
model. New cities in the Central
Coastal area could be served by a
reserve supply available to the
San Francisco Bay area, by develop-
ing local streams, desalting, and
water reclamation; and those in the
San Joaquin Basin could be served
in part by supplies from the San
Francisco area and by the proposed
East Side Division.
From the analysis of the water
demand-water supply relationships
for the "base" projection and the
three hypothetical models it can
be concluded that: (l) no matter
how the population may be distri-
buted in the future, demands for
developed water will remain essen-
tially the same, and it will be
primarily a matter of the optional
sources of water supply and
variation of patterns and costs of
transportation of supplies to areas
of need (Table 14 ) ; (2) the water
supplies available from existing or
definitely planned facilities would
be some 5 million acre-feet per
year short of satisfaction of 2020
demands, thus requiring development
of 5 million acre-feet annually frctri
new sources (see Table 8 in
Chapter VI); and (3) as compared
with the "base" projection there
would be a reduced opportunity for
sea water conversion for Models
"A" and "C", because of their
greater inland concentration of
population.
Waste Disposal
The concept of new cities offers an
opportunity for applying a compre-
hensive systems approach to the
entire problem of waste management.
In existing urban areas, corrective
measures generally are not taken
until considerable damage has
already been done to the environ-
ment. In a new city, however, waste
management facilities can be
designed concurrently with the
-176-
total urban coinplex so that the
most safe, esthetically pleasing
and efficient results can be
obtained. With proper zoning and
other controls over growth and
types of development, facilities
for disposing of wastes need never
become inadeauate.
New cities in coastal locations
would present about the same waste
water disposal problems that would
be e>:pected if an equivalent devel-
opment should take place adjacent
to existing coastal metropolitan
areas. The better quality waste
waters could be reclaimed for
selected reuse applications, such
as environmental enhancement
projects or ground water recharge
with the poorer quality water dis-
posed of in the ocean after ade-
quate treatment. Carefully designed
deep ocean disposal of adequately
treated waste water should cause
little ecological degradation and
may be beneficial in some areas
where present nutrient levels are
not adequate for desirable bio-
logical growths. The future,
however, holds the possibility of
much greater recycling of waste
water.
In the Central Valley large con-
centrations of people and the
industrial base to support them
could present major waste water
management problems . The problems
would intensify with distance from
the ocean as the ocean is the
ultimate natural repository of
wastes, and added mineral loads in
the water supply must be removed or
find their way to the ocean.
Water reclamation would appear to
be an essential element of any
waste vjater management plan for new
cities in the Central Valley.
Excessive algal growths could cause
particular damage to fisheries,
recreational uses and esthetics.
On the other hand, nutrients
retained in the treated effluent
when used for irrigation help meet
fertilizer requirements and further
reduce nutrient concentration in
the return water. Overall salt
loads returned to streams would
remain about the same with or with-
out a reclamation phase, however,
because neither treatment methods
nor irrigation would reduce dissolved
minerals in the waste water.
In the Colorado Desert area disposal
of waste water from large population
centers may be even more complex
than in the Central Valley. Waste
effluents cannot be discharged into
the Colorado River without adding to
the already highly dissolved salt con-
centrations of the river. One solu-
tion that appears reasonable would
be to allow waste water, after bene-
ficial reuse, to drain into artifi-
cial salt lakes where evaporation
would concentrate the salts and no
further use would be intended. Sites
would have to be selected where per-
colating highly mineralized water
would not degrade usable ground
water supplies. The ecologic impact
of such new sinks would require
study. Deep-well injection of waste
water may be a possible alternative
to evaporation lakes.
The problem of disposal of solid
wastes is one which is growing more
intense as our society becomes more
affluent, complex and sophisticated.
Solid waste disposal covers a wide
range, including garbage, trash,
clothing, furniture, automobiles,
other miscellaneous household and
commercial discards, debris from
building construction or demolition,
sewage sludge, agricultural wastes,
industrial refuse, and last but not
least, hazardous wastes such as
explosives and radioactive materials.
While production of solid wastes
presumably would be the same,
irrespective of population distri-
bution, the disposal sites would be
substantially influenced.
At the present time many methods of
handling solid waste are being
experimented with, including land fill,
composting, improved methods of
Incineration, dumping at sea,
destructive distillation, pyrolytlc
decomposition, wet digestion or
combinations of these techniques.
Most of the disposal methods create
■177-
further pollution problems in other
areas, i.e., land fill may pollute
underlying ground water and may
produce gaseous or other noxious
effects, and sea dumping may pollute
coastal areas .
Electric Power
Requirements
In the "base" projection it was
assumed that the primary source of
additional electric power in the
future would be from steam electric
plants, mostly nuclear. In gen-
eral, the plants would be located
along the coastline, because of the
need for large quantities of cooling
water and because most of the popu-
lation, and therefore power require-
ments, would be located in the
coastal areas.
The hypothetical models would, in
general, move the population inland.
However, it is anticipated that the
location of powerplants would remain
along the coastline, with the power
transmitted to Inland areas of need,
as necessary. This would require
the construction of substantial
transmission facilities of high
capacity. Significant environ-
mental issues would be involved.
It is considered that the popula-
tion dispersal would not have a
significant effect on overall power
requirements .
Dispersal of population to Northern
California probably would be the
most advantageous from an electric
power standpoint. With the increase
in population in Northern Califor-
nia, plants could be moved farther
north into less populous coastal
areas. In regard to transmission,
power that would be wheeled to
Southern California over the exten-
sive grid traversing the valley
could be absorbed enroute by con-
struction of minimum facilities.
In the case of population increase
along the foothills of the Sierra
in Central California, extra trans-
mission would be required from the
coastal powerplants to the Sierra
foothills. However, the major
north/south bulk transmission grid
in the Central Valley would minimize
the additional transmission facilities
which would be required.
The most difficult possibility with
regard to electric power would
result from dispersal of the popula-
tion into the southern portion of
the State. In this assumption,
large numbers of people would be
located in the desert areas in the
Colorado Desert and the southern
portion of the South Lahontan area.
This would require substantial
amounts of transmission facilities
to serve the people in the desert
areas . Due to the high population
density of the Southern California
areas, the addition of transmission
facilities is difficult from an
environmental as well as practical
standpoint, and quite expensive. The
southern dispersal of population,
particularly to the desert areas,
would require special attention
with regard to electric power.
Other Considerations
Population dispersal would have an
impact on a number of environmental
and other factors which were not
considered in the analysis of the
hypothetical models. However, other
state agencies provided some insight
on air pollution and transportation as
related to population distribution
patterns .
V/ith regard to air pollution, the
Office of Planning and Research is
undertaking a study to evaluate the
impact of alternative population
distribution patterns. It is antic-
ipated that the Air Resources Board
and other state and local agencies
will be involved in providing a
detailed assessment of this problem.
At this point it is possible to do
no more than draw attention to the
major issues concerning air pollution
and to hypothesize as to the relation-
ship between population distribution
and the problems of air pollution.
Land use and population policies can
be utilized to control the quantity
of pollutants emitted in an area.
-178-
with a substantial effect on air
quality. Generally the greater the
population in an area, the greater
the number of sources and the total
emissions. Thus, prevention of
concentrations of harmful pollutants
may necessitate control of one or
more of the following: (l) the
total number of people in an area,
(2) the population density, and
(3) the location, size, number, and
strength of sources of pollution.
Meteorological conditions determine
the amount of air available to
dilute concentrations of pollutants
emitted to the air. Therefore,
population policies which locate
people in areas with favorable
meteorological conditions will be
beneficial in elim.inating future
pollution problems within the State.
Generally, dilution is greater along
the California Coast than Inland
and greater in Northern California
than Southern California. The
implication is that the air pollu-
tion problem can be reduced in
intensity in metropolitan areas
through population dispersal; but
insufficient knowledge is available
to enable a quantitative determina-
tion of the overall impact.
In our present automobile -oriented
society, highways have served a
dual role of reacting to develop-
ment pressures whil^e at the same
time stimulating further develop-
ment in and adjacent to the areas
served. The approach being investi-
gated by the Office of Planning and
Research suggests new transportation
priorities and probable shifts of
resources .
All three models contain population
redistribution centers within the
Pacific Coastal Mountain Ranges to
one degree or another. Primary
corridor linkages in this area lie
on a north-south axis, with only
limited east-west connections to
the central interior. Expansion of
the number of large urban centers
in the coastal area will require
expansion of the north-south
corridor facilities. Further,
vastly Improved connections between
the coast and the central interior
probably would be essential to
improve communications between these
two areas.
Current transportation corridors in
the Sierra-Cascade foothills area
lie on a north-south axis on the
valley floor. Development of large
urban centers within the foothills
areas would require expanded trans-
portation facilities within the
north-south corridors as well as
improvem.ent of east-west corridor
connections to urban centers on the
valley floor and in the North and
Central Coastal areas .
Development of new urban centers in
the southern portion of the State
would require expansion of the
corridor facilities between the
desert interior and the southern
coastal area. Improved north-south
corridor facilities within the
southern coastal zone would probably
be necessary to maintain an adequate
level of intraregional com,municatlon.
Expanded north-south corridor facili-
ties between Southern California and
Northern California areas most likely
will be necessary to accommodate the
demand generated by the growth
centers in these respective regions.
Transportation is therefore easily
identifiable as a major factor
impacting upon population distribu-
tion. The type, speed, cost, con-
venience and com.fort of various
transportation modes can signifi-
cantly affect the distribution of
population and land uses.
In summary, the impacts of popula-
tion dispersal discussed in this
chapter are based only on very
cursory examination. With exception
of the Impact on water demands, the
conclusions that can be drawn are
more significant in the questions
raised rather than in definitive
information. They point out the
need for careful study of any pro-
posed population center to evaluate
meaningfully the potential problems.
It is apparent that suggestions to
direct people to areas of surplus
water involve various problems, all
of which must be considered together.
-179-
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LIBRARY, UNIVERSITY OF CALIFORNIA. DAVIS
D4613-1 (5/02)M
STATE OF CALIFORNIA
THE RESOURCES AGENCY
DEPARTMENT OF WATER RESOURCES
WATER RESOURCES DEVELOPMENT
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