Restoration Project Draft EIS/EIR Jan 2000 |
During the past eighteen months, the U.S. Department of the Interior, working in
partnership with the Salton Sea Authority and many other federal, state, tribal, local and
academic entities, has conducted environmental, feasibility, and scientific studies in preparation
of a Draft Environmental Impact Statement/Environmental Impact Report (DEIS/EIR) on the
Salton Sea in California. This overview, intended to compliment the Draft EIS/EIR being
transmitted to Congress and released to the public, provides a general summary of the
preliminary findings of the studies as well as offers comments on potential future actions for
restoration.
Transmittal of this document and the Draft EIS/EIR, along with its accompanying
Strategic Science Plan and the Bureau of Reclamation's Alternatives Appraisal Report,
constitutes the Secretary's submission of recommendations and the results of the study as
described in the Salton Sea Reclamation Act of 1998 (P.L. 105-372), Section 101(b)(1)(B).
In December 1997, Secretary of the Interior Bruce Babbitt visited the Salton Sea to
consult with state, local, tribal, and Congressional officials about addressing the challenges
presented by degrading conditions at the Salton Sea. Finding a consensus to improve the health
of the Sea among these parties, Secretary Babbitt proposed that the parties: (1) create a joint
governmental coordinating mechanism to focus the efforts of the various governmental entities;
and (2) undertake an environmental review process under NEPA and CEQA to identify and
evaluate specific options for addressing the health of the Sea.
In the months following the intergovernmental consultation at the Sea, the California
congressional delegation worked closely with the Department of the Interior, the Salton Sea
Authority, the Torres Martinez Indian Tribe, and the State of California to craft legislation that
would establish parameters and set an expedited schedule for this review process. Ultimately,
Congress passed and the President signed into law the Salton Sea Reclamation Act of 1998 (1998
Act) which established and defined the environmental review and alternatives analysis process
which has been ongoing for the past eighteen months. Eighteen months is a truly ambitious
timeline to attempt to gain an adequate understanding of such a unique and complex ecosystem.
Both the Administration and Congress agreed, however, that acting quickly to evaluate and
assess the health of the Sea would be critical to the effectiveness of any future restoration effort
at the Salton Sea.
Partners, Roles, and Process
Preparation of the DEIS/EIR has been co-led by the U.S. Department of the
Interior/Bureau of Reclamation and the Salton Sea Authority. (The Salton Sea Authority in
California is comprised of the Coachella Valley Water District, the Imperial Irrigation District,
the County of Riverside and the County of Imperial, and includes ex-officio representation by theTorres Martinez Desert Cahuilla Tribe and State and federal agencies.) As Secretary Babbitt
proposed at the Sea in late 1997, this work has been guided and supported by two entities created
for this effort: (1) the Salton Sea Research Management Committee and (2) the Salton Sea
Science Subcommittee.
The Research Management Committee is comprised of five members representing the
Secretary of the Interior, the Governor of California, the Salton Sea Authority, the Torres
Martinez Desert Cahuilla Indian Tribe, and the California Water Resources Center. The
Research Management Committee has served the role of providing policy guidance, assisting in
directing research priorities, and identifying resources necessary to carry out studies and prepare
the DEIS/EIR.
The Science Subcommittee was created to provide scientific evaluations and
recommendations required to guide the NEPA/CEQA process to sound conclusions regarding
potential alternative actions for mitigating the degradation of the Salton Sea ecosystem and
restoring recreational, wildlife, and economic values. The Science Subcommittee's membership
comprises primarily science and engineering representatives from a wide range of federal, state,
tribal, local, environmental, and academic entities with an interest in the Sea. Regularly held
meetings of the Science Subcommittee have been open to the public to allow for general access
to the process. In addition, a number of public workshops targeting varying interests and
focusing on specific issues have been held to further encourage public involvement.
Public comment also has a statutory role in crafting an Environmental Impact Statement.
Simultaneous to the transmittal of the DEIS/EIR to Congress, the Draft shall be made available
for public input during a comment period of at least 90 days. Public input, along with detailed
engineering analysis of the alternatives, will aid in further refining the Draft.
The Torres Martinez Desert Cahuilla Tribe has played a unique role in informing our
analysis. The Tribe has continuously occupied the region for hundreds of years and maintains a
unique connection with the cultural and natural history of the region. The Tribe administers
thousands of acres which include wetlands, critical habitat, lake shore and lands underlying the
Sea. Economic development, recreational initiatives and comprehensive environmental programs
make the Tribe a significant and unique partner in the restoration of the Salton Sea.
Restoration of the Salton Sea has inherent international implications that involve Mexico
as an important partner. Given factors such as international migratory bird treaties, consideration
of pumpout options that contemplate outfall in Mexico, the international aspects of the New and
Alamo Rivers, and other facets of restoration, Mexico has had an important role in the current
process and must continue to be actively included in the formal comment process and any
subsequent implementation process. Mexican representatives from SEMARNAP and CILA
(along with U.S. representatives from the International Boundaries and Water Commission) were
invited to participate through the Science Subcommittee. Increased involvement from Mexican
officials will be important to future Salton Sea restoration activities and processes.
Background and the Importance of the Salton Sea
The Salton Sea, spanning Riverside and Imperial Counties in Southern California, is a
uniquely troubled yet valuable natural resource to humans, to wildlife, and to the agriculture
industry. Throughout geologic time, dating as far back as 1.6 million years ago, the "Salton
Trough" has periodically been flooded creating bodies of water, and in turn evaporated due to
lack of a consistent inflow source. Rising and receding water levels were common in this
prehistoric "Lake Cahuilla" due to periodic flooding and the meandering channel of the Colorado
River. Inflows to the Trough would cease for extended periods, at times leading to complete
evaporation of the lake, with the most recent complete evaporation of Lake Cahuilla probably
taking place about 300 to 500 years ago. However, as recently as the 1800s, a number of smaller
and more short-lived lakes were witnessed in the Trough a different times. The current Sea was
created between 1905 - 1907 when a private irrigation dike was breached by flood waters
allowing the entire flow of the Colorado River to flow into the Trough for approximately 18
months. But the current Salton Sea is not just another phase in the cycle of flooding and
evaporating in the Trough; rather, as the Strategic Science Plan explains, the Sea today is the
product of more permanent inflow sources, the expanded presence of humans, and Colorado
River flood control dams. Presently, the Sea has become a critical and incomparable wildlife
resource, a valuable recreational resource, and an important element of the regional agricultural
industry.
The Salton Sea is an incredibly rich and biodiverse natural resource. The Sea is an
extremely productive fishery -- perhaps the most productive in the world. This ecosystem also
supports some 400 species of birds; only the Gulf Coast of Texas hosts more species of birds in
the United States. Three endangered species -- the Desert Pupfish, the Yuma Clapper Rail, and
the California Brown Pelican -- also inhabit the Sea. The Salton Sea hosts such a complex
ecosystem that during the past 18 months during which studies were ongoing, 200 new species,
never known to exist at the Sea, were identified. The Sea is perhaps most important to a large
segment of the migratory birds of the Pacific flyway. Since the creation of the Salton Sea,
significant losses have occurred in interior wetlands that might otherwise have provided
alternative sites for migratory birds. In California in particular, about 95 percent of interior
wetlands have been lost, leaving the Salton Sea as the sole remaining location for many species
based on food availability and travel distances between stopover points. In this regard,
preserving a healthy Salton Sea is critical to local, regional, and international migratory bird
conservation, and to global biodiversity in general.
The Salton Sea also offers a bounty of recreational opportunities. Recreational use at the
Sea traditionally has included hunting, sportfishing, boating, birdwatching, and photography. As
recently as 1985, visitors to the Salton Sea annually exceeded those at Yosemite National Park.
Even with the troubled state of the Sea, more than 250,000 people visited the Salton Sea
Recreation Area between 1997 and 1998. These figures are not entirely surprising given that
approximately 6% of the U.S. population lives within driving distance of the Salton Sea. The
potential economic values of a healthy Sea that draws recreational visitors to the Sea and
surrounding communities and the region clearly are significant.
Agriculture makes up a major portion of the economic base in Imperial County and
eastern Riverside County which, in turn, are important producers of vegetables and other produce
to the entire nation, particularly in winter. Agriculture in the region is a $1 billion a year industry
and provides one in three jobs to the local residents. Adequate drainage is an important element
of this agricultural economy, and the Sea historically has provided, and continues to provide, an
important repository for such drainage. This agricultural drainage water represents a major
source of inflow to the Sea.
It is important that restoration efforts recognize that inflows into the Salton Sea through
agricultural drainage water are likely to decrease over time concurrent with the phase-in of new
water conservation practices in the Imperial Valley. The DEIS/EIR process to date has
considered this likelihood (as the 1998 Act directed) by contemplating various inflow levels as
low as 800,000 acre-feet/year. In addition, the Department considers this conservation to be
extraordinarily important, particularly as pertains to the necessity that the State of California
reduce its reliance on the Colorado River to a level that is consistent with the "Law of the River."
It also is important to note that the Salton Sea is an important component of a large and
complex ecosystem. The New River, for example, which flows north into the Salton Sea from
Mexico, is a stressed river system that has been the subject of significant clean up initiatives by
the U.S. Environmental Protection Agency, the U.S. Bureau of Reclamation, and others.
Likewise, because the Salton Sea is maintained by Colorado River flows, it is part of a larger
Colorado River ecosystem which includes the Colorado River Delta. Restoration efforts to date
have been and should continue to be crafted and guided with this recognition of the Sea as part of
a larger ecosystem.
Balancing the values of recreation, agriculture, and wildlife, the Salton Sea is truly a
contemporary ecological challenge. Particularly in the West, the future surely will offer many
challenges in terms of balancing social, economic, and environmental values in the face of
limited water availability. Working to ensure biodiversity while maintaining recreation and
economic opportunities will have practical applications well into the 21st century as demand
grows on limited water supplies. In this way, the Salton Sea represents a unique proving ground
such that the lessons learned here likely will be translatable to a variety of future issues and other
environments.
Scientific Studies to Date and the Need for Ongoing Science
The Science Subcommittee (SSC) was created to provide a sound scientific foundation
upon which management decisions can be based in considering alternatives for achieving
restoration project goals. The creation of this Science Subcommittee and its work parallel to the
options evaluation process represents a new and innovative means of breathing real-time science
into an EIS/EIR evaluation process. Further science is undoubtedly needed, however, the
alternatives and options discussed in the DEIS/EIR are better refined due to the input of the
Science Subcommittee into the evaluation process.
Specifically, the Science Subcommittee undertook four primary charges; the SSC: (i)
evaluated existing information on the Sea to determine what already was known, what needed to
be verified, and what critical data gaps existed; (ii) initiated focused investigations to describe
the current "State of the Sea"; (iii) initiated focused investigations to gain information needed to
address major remediation issues; and (iv) developed a strategy for providing effective long-term
scientific support for restoration and future management of the Sea. To these ends, the Science
Subcommittee identified needs and made recommendations that resulted in contracting for over
$5 million in studies which have contributed to refining the alternatives discussed in the
DEIS/EIR. In addition, the studies will provide the foundation for establishing baseline data for
the Sea, against which restoration efforts can be measured and redirected as necessary.
Determining the "State of the Sea" is of critical importance to any successful restoration
project as accurate baseline data will serve, through adaptive management, to guide project goals
and measure the effectiveness of remediation efforts in terms of restoring and protecting the
ecosystem. The Science Subcommittee's assessment examines and describes the fishery, birds,
water quality, critical habitat, vegetation, and contaminant loads among other things, and
provides the most comprehensive understanding of the Sea to date.
A number of studies have been undertaken in developing the State of the Sea which have
provided a wide range of results. Studies identified as necessary by the Science Subcommittee
and subsequently conducted include evaluations of: (1) physical limnology (water and sediment
chemistry); (2) biological limnology (algae, invertebrates and plankton i.e., food web
components); (3) sediment characteristics and contaminant levels; (4) fish populations (including
the endangered desert pupfish); (5) bird populations; (6) vegetation delineation; and (7) algal
toxins and biological pathogens in the waters and sediments of the Sea. In turn, for each of these
evaluation areas, synthesis documents were developed and provided to inform the project
evaluation process. Of particular note, these investigations were conducted in such a manner as
to provide preliminary findings on a real-time basis in order to assist in guiding project
evaluation, rather than providing a final report on findings well after the investigations were
completed, as is typical in studies of this nature.
After evaluating existing data and identifying gaps therein, the Science Subcommittee
made recommendations to award contracts for a number of focused scientific investigations to
describe the current state of key components of the ecosystem, as well as four studies of fish and
avian mortality. (Studies were funded through the Salton Sea Authority by a research grant from
the U.S. Environmental Protection Agency.) In addition, eight issue-specific documents were
prepared by the Science Subcommittee to address issues that arose through the project evaluation
process. The combination of these investigations and numerous meetings involving scientific
evaluations of various aspects of the Sea provides the most comprehensive evaluation of the
Salton Sea to date. The value of these investigations became self-evident as many of the findings
differed from commonly held perceptions and existing conventional wisdom about the Sea.
Through these studies, the Science Subcommittee injected current scientific information into the
project evaluation process, replacing conjecture and data gaps that previously existed.
The investigations requested by the Science Subcommittee resulted in a variety of
findings relevant to restoration, many of them unexpected. Key findings are highlighted below:
* Fish populations, thought to be very depressed, are actually abundant; in fact, the
Salton Sea may be the most productive fishery in the world.
* Pesticides, presumed to be a major problem within the Sea, are not; most pesticide
levels in the sediments and waters of the Sea were found to be at below detectable
levels of the analytical methods used.
* Though algal toxins have long been thought to be a major cause of fish and bird
mortality at the Sea, investigations failed to reveal any evidence of algal toxins
causing either fish or bird kills.
* Extensive data has been gathered on fish populations and bird use of the Sea
broken down by species, geographic location and time of year; this data will be
important to identifying habitat areas that must be protected in the restoration
process.
* The distribution of sediments was mapped by particle size and contaminant levels
in those sediments evaluated. Findings were notably different than anticipated.
Contaminant levels in general were minimal relative to hazard assessments except
for a limited number of hot spots. In addition, the deposition of different types of
sediments (clays, sand, slit) did not confirm expectations. These sediment
findings are important relative to potential dredging activities and use of
sediments as construction materials, evaluation of hazards associated with
sediments that may become exposed due to receding water levels, and for
evaluating the consequences of sediment redistribution that might occur as a result
of changes in circulation patterns of the Sea due to constructed impoundments and
other features of any restoration project.
* Contrary to perceptions and claims that the Sea is highly contaminated with
enteric forms of bacteria and other microorganisms capable of causing human
disease, findings have been primarily restricted to bacteria of the genera
Aeromonas and Vibrio. These bacteria are primarily optimistic invaders that have
no major human health significance.
The Science Subcommittee has prepared a "Strategic Science Plan" (SSP) as an
accompanying document to the DEIS/EIR which addresses many of these issues in detail. The
SSP provides background and historical information on the Sea and the region, highlights the
activities and accomplishments of the Science Subcommittee, and lays the conceptual framework
for establishing a continuing Salton Sea science effort linked to restoration of the Sea.
Specifically, the SSP provides recommendations for the development, function, and
oversight of a pragmatic science effort to support long-term management actions for restoring the
Salton Sea. The SSP makes four primary recommendations for future science activities:
Each of these proposals are discussed in detail the Strategic Science Plan (a companion
document to the DEIS/EIR). Given the complexity of the Salton Sea ecosystem and the clear
need for further science to better understand and address the challenges presently degrading the
ecosystem, the recommendations for ongoing science contained in the SSP will be an integral
component of any restoration effort.
Current Status of the Sea and the Need for Action
The Salton Sea ecosystem is highly complex and faces many stressors including nutrient
loading, increasing salinity, oxygen depletion, temperature fluctuations and others. These water
quality issues taken individually are problematic at a minimum, but in combination, they threaten
the ability of the Salton Sea to sustain its fishery, and thus the fish-eating birds of the Sea.
Expected reductions in inflows into the Sea in the future will complicate the challenge.
The most visible and perhaps best known malady at the Salton Sea involves wildlife die
offs. The massive fish and bird kills that have plagued the Sea obviously signal trouble for the
future of the wildlife, but they also bring a host of unpleasant sights, odors, and other side effects
to the Sea and the surrounding area. Preventing such wildlife die offs in the future will
inevitably mean improving water quality, which is of obvious importance to the fish and
ultimately the birds. Of course, addressing water quality alone will not save the Sea, but salinity,
specifically, presents the most immediate water quality threat to the wildlife at the Sea. If rising
salinity levels are not addressed and addressed soon, the sport fishery cannot survive, nor can the
birds that depend on the fish as food, thus rendering (for those species) other stressors moot. In
turn, these losses will negatively impact recreational uses of the Sea, as well as economic returns
from those activities.
At present, the Salton Sea's salinity measures about 44,000 mg/L, as compared to 35,000
mg/L for ocean water. Because the Sea has no natural outlet, the only way for water to escape is
through evaporation (leaving salts behind in the Sea) which further increases salinity levels. To
put this in perspective, by virtue of the salinity content of inflows and the effects of evaporation,
the equivalent of a trainload of salt one mile long pours into the Salton Sea every day. It cannot
be predicted for certain, but science suggests that once the sea crosses the 50,000 mg/L level, the
ecosystem will begin to collapse beyond repair. Logically, a reduction in inflows to the Sea
would accelerate this process. Salinity reduction must be part of a larger scientifically-based
solution that has the benefit of a fuller understanding of the Salton Sea ecosystem, but salinity
presently is the most pressing danger facing the Salton Sea.
It is important to note that the ills of the Sea become more difficult to correct the longer
they are left unchecked. Much as paying down an interest-accruing loan begins with the bulk of
the early payments servicing interest rather than principal, the longer remediation action for the
Sea is delayed, the more difficult and expensive it will be just to return the Sea to a state that can
sustain project goals, let alone maintain it as such. Stabilizing the salinity at the Sea at an
acceptable level will be one ultimate goal of any restoration effort; however, before salinity can
be stabilized at an acceptable level, the amount of salinity must be reduced, and the longer action
is delayed, the greater the needed reduction will be.
Even if action were decided upon today, given administrative, budgetary, and logistical
constraints, it would likely be eight or ten years before any appreciable results could be realized.
The problems at the Sea are worsening, the stress on the ecosystem is increasing, and the window
for taking action to save the Sea is closing.
Public Scoping and Criteria for Evaluating Alternatives
The eighteen-month DEIS/EIR effort began with an extensive public scoping process.
Two sets of public workshops were held in several locations over a period of several months
through which extensive public input was sought and was received. Five goals for the project
were established and refined during this period:
Alternatives to address the Sea's salinity and elevation problems have been considered
and proposed for over four decades. During this time, several reports have been compiled by the
Bureau of Reclamation, the State of California and various local agencies. Many alternatives
examined in those reports as well as others were considered during the public scoping phase of
the current effort. However, a comprehensive approach to restoration was sought, as many
stakeholders expressed skepticism towards the traditional focus on salinity and elevation alone,
particularly with regard to wildlife resources. Of the scores of alternatives proposed over the
years, thirty-nine alternatives were carried forward for analysis in a pre-appraisal report.
Alternatives included evaporation ponds, enhanced evaporation systems, pump-in and pump-out
options, and water quality treatment alternatives.
To narrow the range of alternatives to a reasonable number for consideration in the
EIS/EIR and to measure and rate potential alternatives consistently, an evaluation criteria process
was established and employed. Evaluation criteria and elimination criteria were weighted by a
group of local, state and federal stakeholders in a consensus process. The criteria and their
weightings were presented to the public during a series of public workshops. The resulting
evaluation criteria, in their weighted order, are:
Each remaining alternative was rated against each evaluation criterion. The ratings were
multiplied by the relative "weight" of the evaluation criterion and summed. Six alternatives rose
to the top of the analysis. Further engineering and cost analysis refined the six alternatives,
resulting in the five phase one alternatives considered in the DEIS/EIR. Other alternatives which
showed promise were considered as part of Phase Two, long-term restoration actions, and
included in a more generic fashion in the DEIS/EIR.
A multi-agency task force was established to address objectives not fully satisfied by the
major engineering alternatives. Objectives such as implementing and maintaining clean
shorelines and reducing the occurrence of large-scale fish die-offs were not adequately addressed
by the major engineering alternatives. The Alternatives Enhancement Task Force considered
projects and programs that were submitted, and developed a few additional projects and
programs to address these issues. Several of these projects and programs are reflected in the
DEIS/EIR, generally referred to as Common Actions.
The resulting actions were compiled into a series of composite alternatives. The
alternatives share all of the Common Actions, such as shoreline clean-up, fish harvesting, the
North Wetland Habitat, a wildlife disease program, and improved recreational facilities. The
major difference among the alternatives is how they address salinity and elevation objectives.
Additionally, there are three "no action" scenarios, reflecting possible inflow scenarios over time.
One no action scenario assumes that the current inflow into the Sea remains the same over time,
at approximately 1.36 million acre-feet per year. Another no action scenario assumes an
approximately 300,000-acre foot reduction in inflows to the Sea, and the last no action scenario
responds to a level required to be considered in the legislation resulting from a 563,000-acre foot
reduction in inflow.
Even after the official public scoping process, during the first few months of the 18-
month period, public input was actively sought. Additional workshops were held throughout the
process, and workshop agendas generally paralleled development of the DEIS/EIR, from goal
and objective setting, to evaluation criteria development and alternative identification, to
application of the evaluation criteria and refinement of the alternatives, and lastly to presentation
of alternatives considered in the DEIS/EIR. In addition to the extensive public workshop
program, newsletters were periodically prepared and distributed to every interested party who
attended workshops and registered. Special workshops were held with members of the
environmental community. On several occasions, workshops were co-sponsored with the
Audubon Society and involved several other environmental non-governmental organizations.
Additional public workshops/hearings will be held as the formal Draft EIS/EIR review process
begins.
Through this extensive public outreach process, the above-described criteria for
evaluating alternatives were developed, ultimately resulting in the alternatives for action
considered in the DEIS/EIR.
Alternatives for Restoration
Over the past eighteen months, many potential restoration alternatives have been explored
and considered. Through public scoping, general engineering and feasibility analyses,
consideration of input from the Science Subcommittee, and considerations of economic
practicality (as directed by the 1998 Act), a number of alternatives have been eliminated while
several others have been brought forward for further consideration in the DEIS/EIR.
Under the expedited eighteen month process, it proved neither possible nor prudent to
identify a clear and decisive final solution for the Salton Sea. The Sea is a truly massive body of
water: with 365 square miles of surface area and approximately 7.5 million acre feet or 2.445
trillion gallons of water, it is roughly twice the size of Lake Tahoe. Given the complexity of the
Salton Sea ecosystem, the physical environment, and the sheer volume of the Sea, addressing the
serious water quality problems at the Sea is an engineering and scientific challenge of historic
proportions with enormous cost and feasibility considerations. Considering these complex and
interrelated challenges, a phased approach to restoration as contemplated in the DEIS/EIR, that
allows further science to inform the process and guide restoration, will likely yield the highest
possible degree of success.
The DEIS/EIR provides the framework for a phased or staged approach to restoration,
using a combination of alternatives. The phased approach to restoration is premised on the
notion that certain components of restoration can be more readily implemented presently while
others may require further scientific or engineering analysis. In addition, a successful and
enduring Phase One project could preclude the need for a Phase Two project. To this end, the
DEIS/EIR espouses a suite of common actions followed by a two phase approach: (i) common
actions that can be begun almost immediately (as soon as funding is available), and that will
complement any future projects; (ii) Phase One or "medium-term" restoration projects designed
to reduce and stabilize salinity for at least 30 years; and if necessary, (iii) Phase Two or "long-
term" restoration projects that involve supplementing inflows to the Sea, creating displacement
structures for elevation control, stabilizing the salinity level for 100 years or more, and/or more
substantial and longer lasting export options.
The first step involves actions, described in the DEIS/EIR as "Common Actions," that
generally can be taken without further significant delay. These actions would be complementary
to any restoration alternative selected and include: improving recreational facilities;
implementing a shoreline cleanup program; undertaking an integrated wildlife disease program;
implementing a fish harvesting program to reduce internal nutrient loading and fish population
density; and instituting a long-term science program which will serve to provide a more complete
understanding of the ecosystem and will provide benchmarks to guide and evaluate the
effectiveness of restoration actions.
Phase One alternatives are medium-term actions aimed primarily at reducing and
stabilizing salinity levels and would have an effective life of at least 30 years. However, it is
worth noting that Phase One alternatives may have a life well beyond the 30 year target and as
such, could potentially render construction of a Phase Two project unnecessary. Alternatives in
Phase One include: (1) construction of an Enhanced Evaporation System (EES) project, a system
that sprays a fine mist of water into the air to accelerate evaporation and create a saline
precipitate; (2) construction of one or more evaporation ponds that would concentrate salts
within their boundaries to reduce salinity in the Sea (and also could potentially serve as a
displacement mechanism to control the Sea's elevation); and (3) a combination of an EES system
with evaporation ponds. The DEIS/EIR contemplates various locations for these alternatives
including within the current boundaries of the Sea, at the Salton Sea Test Base property on the
southwest shore, and north of Bombay Beach on the eastern shore. Phase One alternatives could
be permitted, constructed, and operational within approximately 8 - 10 years and would cost
between $305 - $543 million with annual operating costs ranging from $1.7 to $22.8 million.
Phase Two alternatives, if necessary, would consist of major construction projects
designed to further enhance salinity control, control elevation, supplement inflow, and/or create
outflow. Because future inflows to the Sea may potentially be reduced, the DEIS/EIR
contemplates alternatives under three possible inflow scenarios: the present level of 1.363
million acre feet per year (maf/yr), a reduction of 300,000 acre feet to 1.063 maf/yr, and a bottom
level of 0.8 maf/yr. While these levels obviously do not reflect the universe of possible inflows,
the range provides a useful perspective through which to consider restoration alternatives. Phase
Two alternatives include: (1) identification of a reliable source of lower-salinity water and
construction of an importation system to dilute the Sea's water; (2) construction of an export
system to compensate for the Sea's lack of outflow; (3) construction of expanded capacity for
salinity reduction mechanisms employed under Phase One; and (4) construction of displacement
structures to control elevation (note: it is possible, depending on reductions in inflows to the Sea
and the rate at which they occur, that a displacement structure could be necessary late in Phase
One). These long-term projects would become more necessary as inflows to the Sea are reduced
over time and would have an effective life of no less than 70 - 100 years. Phase Two project
alternatives would require a significant amount of time to design and construct and have wide
range of estimated construction costs, varying from as low as $73 million, all the way up to $2.8
billion.
As a footnote, it should be recognized that on-going science efforts could identify
restoration project needs that have not been uncovered or discussed in the DEIS/EIR, thus
creating the need for additional restoration alternatives. Science must be allowed to continue to
shape and inform the process through adaptive management, and as such, restoration projects
must be somewhat flexible to allow for periodic "course corrections" provided by science.
Conclusions and Recommendations
The DEIS/EIR does not specify a preferred alternative. Rather, it sets forth a menu of
restoration options in various combinations. Public comment and further engineering analysis
will aid in further narrowing the field of alternatives. In addition, the Department believes that
some comments and recommendations based on existing information are appropriate at this time.
First, the Department recognizes the Sea as an important natural resource with great value
for wildlife, recreation and agriculture. As such, the Department recommends, at a basic level,
that the Salton Sea should be saved; a no action alternative is not acceptable.
As discussed in this document and in the DEIS/EIR, there are some restoration elements
that will complement any ultimate restoration project. The Department recommends that these
common actions (recreational facilities enhancements, shoreline cleanup program, integrated
wildlife disease program, fish harvesting program, and long-term scientific monitoring and
management program) be undertaken as soon as practical. While they alone cannot cure the ills
of the Sea, these actions are important first steps to returning the Sea to a healthy state and a
more desirable resource.
To aid in the selection of a medium-term project, the Department recommends that pilot
projects to assess the effectiveness and practicality of Phase One alternatives be undertaken with
all due haste. The Department further recommends that as soon as results are available from the
pilot studies, a Phase One project should be implemented to begin to address the key water
quality parameter that poses the most significant threat to the Sea: salinity. Time is of the
essence for the Salton Sea, and given estimates for startup for such a project, unnecessarily
delaying action will not only make restoration more difficult, but could allow major aspects of
the ecosystem to collapse.
The DEIS/EIR requests comment on the potential use of flood flows from the Colorado
River as available to supplement inflows to the Sea. The Department has potential concerns
about this notion insofar as it may implicate Colorado River management issues that are of
special interest to the Basin States, Mexico, and other stakeholders. We actively invite comment
on this concept; the Department is not taking a position that favors this potential alternative.
The DEIS/EIR lays the framework for a phased approach to restoration and the
Department endorses this notion for a number of reasons. Salinity will cause the collapse of the
Sea's fishery (and kill fish-eating birds that depend on the fishery) if it is not addressed in the
very near future whereas supplemental inflows and elevation control only become necessary in
the future if and when inflows decline. For this reason, a phased approach makes practical sense.
Secondly, it is important to recognize that any project(s) undertaken to remediate the Salton Sea
will require significant monetary commitments from all involved, keeping in mind the respective
capabilities and limitations of all parties. Funding restoration projects in phases over time
equates to a kind of payment plan that makes fiscal sense. Thirdly, an engineering project of this
extraordinary magnitude over such a long period of time will be well served by a phased
approach that can be adapted to fit the changing needs of the Sea. It is impractical at best to
accurately predict at this juncture what the state of the Sea will be in 30 or 50 years; a phased
approach to restoration provides a much more realistic means of addressing the future needs of
the Salton Sea.
Finally, the need for continued scientific monitoring and study bears reiterating. While
the scientific examination during the past 18 months has provided the most comprehensive
assessment of the Sea to date, perhaps the most important understanding that has come from this
work is that we do not yet fully understand the ecosystem at the Salton Sea. Until and unless
more comprehensive knowledge of the Sea's ecosystem is attained, we can never truly restore the
Sea to the levels identified in the project goals. Moreover, without ongoing science and
monitoring, the effectiveness of any future restoration project cannot be accurately gauged. The
work of the Science Subcommittee during the past 18 months is invaluable to the restoration
process, but it is only a beginning and continued science is essential to finish what has been
started. The creation of a dedicated science office to foster this effort, as discussed in the
Strategic Science Plan, is recommended to continue the scientific work.
In summary, restoration of the Salton Sea is an extremely complex challenge that will
require a long-term understanding of the problems facing the Sea, and a dedicated but flexible
approach. Continued partnerships and collaboration between science and project management,
and among federal, state, tribal, and local government entities and others, as well as continued
support from Congress, will be essential for restoration of the Salton Sea to succeed.
Introduction * The Salton Sea is alive and vibrant in terms of biological complexity rather than
nearly dead - more than 200 species (mostly microscopic) not previously known
to exist at the Sea have been identified.
Although the Science Subcommittee's assessment of the Sea is comprehensive relative to
previously existing data, it is basic in terms of what will be necessary to gain a full understanding
of the Salton Sea ecosystem. In addition to providing adaptive management to restoration
efforts, additional science is underway and necessary in order to address the environmental
factors contributing to the causes of disease and die offs among the Sea's wildlife. Given the
present basic understanding of the Salton Sea ecosystem, science can only address the symptoms
of disease, thus being primarily reactive. With a fuller understanding of the ecosystem, science
will be able to address the causes of disease, and thus proactively provide preventive medicine.
Without additional and ongoing science, a permanent solution to wildlife mortality will not be
possible.
Notably, these goals parallel very closely those set forth in the 1998 Act. The act also included
objectives for stabilizing the surface elevation and for reducing and stabilizing the salinity of the
Sea. Salinity and elevation control objectives and other specific objectives were developed and
refined with the help of the Science Subcommittee. These objectives and goals are discussed in
detail in the DEIS/EIR. Ultimately, it is these goals and objectives that will be used to determine
the effectiveness of any actions that are undertaken to improve and sustain the Salton Sea.
Agricultural Interests
Additionally, alternatives which relied upon unproven technologies or that did not adequately
address project goals were eliminated from consideration, consistent with the 1998 Act.
Alternatives which showed promise in addressing some objectives but not salinity and elevation
were considered in greater detail as a part of an alternatives enhancement process (discussed
below).
Wildlife
Elevation
Disposal
Water Quality, Salinity
Water Quality, Other
Operations, Maintenance, Energy & Replacement Costs (OME&R)
Finance Costs
Location
Construction Costs
Sport Fishery
Recreation
Economic Development
Intergovernmental Cooperation
Land
Time to Solution
Time to Construction
Partners
Water Removal
Benefits and Impacts
Posted: January 2000
Webmaster: sha-lcr-webcomments@usbr.gov