Introduction
The
Sacramento River Watershed Program (SRWP) is a stakeholder-driven
effort to restore and protect beneficial uses and maintain the economic
and social vitality of the Sacramento River Basin. Stakeholders
include representatives of local municipalities and districts, local
watershed conservancies, state and federal agencies, water districts,
agriculture, mining, forest products, environmental organizations,
landowners, universities, and technical consultants. The program
was initiated in 1996 by the Sacramento Regional County Sanitation
District (SRCSD), the Central Valley Regional Water Quality Control
Board, and EPA Region IX through federal funding derived from the
Sacramento River Toxic Pollutant Control Program (SRTPCP). The SRCSD
has been awarded $4.4 million in four separate annual authorizations
to perform the tasks included in the SRTPCP workplan. Tasks include
supporting the SRWP and implementing a water quality monitoring
program in the Sacramento River Basin. Significant public and private
support of the SRWP has been provided through in-kind services and
participation in subcommittee activities of the program.
Water
Quality Monitoring Program
A major
emphasis of the SRWP and SRTPCP to date has been on the development
and implementation of an integrated water quality monitoring program
for the Sacramento River Basin. The program was developed through
a subcommittee process which included the following key steps: developing
goals and objectives, identifying and understanding ongoing monitoring
programs, identifying water quality constituents of concern to various
stakeholder groups, developing and evaluating various straw proposals
for monitoring, selecting a preferred monitoring plan which capitalized
on existing monitoring efforts, selecting parties to perform sampling
and analysis tasks, and implementing the monitoring plan. The constituents
monitored under the first-year SRWP monitoring program include:
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water column and sediment toxicity
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bioaccumulative substances in fish tissue (mercury, PCBs, organochlorine
pesticides)
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pathogens (Cryptosporidium, Giardia, coliform bacteria)
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trace metals (mercury, cadmium, copper, chromium, lead, nickel,
zinc, arsenic)
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organic carbon (total and dissolved)
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biological indicators (benthic invertebrates, attached algae,
habitat)
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conventional parameters (e.g., pH, temperature, dissolved oxygen,
hardness, total suspended solids, electrical conductivity)
The
first-year monitoring effort is comprised of regular monitoring
events (monthly, semi-annual, and/or annual) at over sixty sites
on the Sacramento main stem, major tributaries, and selected smaller
tributaries. The long-term goal of the SRWP monitoring program is
to develop a coordinated, cost-efficient, long-term program to identify
the causes, effects, and extent of water quality constituents that
affect beneficial uses, and to develop a baseline for the assessment
of the success of control strategies and improvement projects. Information
from the monitoring program will be used to improve the understanding
of conditions in the watershed. The goal for the first-year monitoring
effort is to determine conditions in the main stem of the Sacramento
River to assess the degree to which beneficial uses are attained
or impaired.
Annual
reports will be produced at the end of each year of SRWP monitoring.
The first-year monitoring effort will be completed in June 1999.
An annual report for the first year will be completed in December
1999. Data from the program will be placed in a publicly accessible
electronic database managed by the Department of Water Resources.
Data will be available over the internet through a SRWP homepage
with links to the Interagency Ecological Program.
Public
Outreach and Education
Another
significant component of the ongoing SRWP is outreach and education
to build support for watershed management activities, establish
links between stakeholders, and promote knowledge and awareness
of the watershed. The Public Outreach and Education Subcommittee
organizes general stakeholder meetings and educational workshops
to achieve these goals. The Subcommittee oversees production of
a quarterly newsletter for the SRWP and monthly calendar of events
for the SRWP and other watershed activities.
Coordination
with Other Programs
The
Sacramento River Watershed Program has been developed in coordination
with a number of ongoing monitoring efforts. These include the Sacramento
CMP Ambient Monitoring Program, the U.S. Geological Survey National
Water Quality Assessment (USGS NWQA) project for the Sacramento
River, Regional Water Quality Control Board toxicity testing in
the Sacramento Valley, the Department of Water Resources Northern
District tributary monitoring program, and the Department of Pesticide
Regulation Dormant Spray Monitoring Program. Coordination has included
adopting compatible sampling and analytical methods, coordinating
sample collections, sharing sampling duties, restructuring program
elements, and agreeing to share data.
Results
of SRWP Monitoring
Results
to date from SRWP sponsored monitoring is limited to fish tissue
and water column toxicity data. Each of these program elements was
started as a pilot study ahead of the first-year monitoring effort,
which began in June 1998.
Fish
tissue results are from a sampling effort performed in September
1997. The work was performed by a team comprised of staff from the
San Francisco Estuary Institute, Department of Fish and Game, and
Long Marine Laboratory at the University of California, Santa Cruz.
Species
tested included white catfish taken from seven sites in the lower
watershed and rainbow trout taken from five sites in the upper watershed.
Parameters analyzed include mercury, PCBs, and chlorinated pesticides.
The purpose of fish tissue monitoring is to determine whether levels
of these chemicals are of concern to consumers of fish, including
both humans and upper trophic level fish and wildlife. Results of
the 1997 fish tissue monitoring effort are summarized in Table
8.1. These results indicate that mercury levels in catfish are
of potential concern, while mercury levels in rainbow trout are
not of concern. Levels of PCBs are of potential concern at some
locations.
Water
column toxicity testing for the SRWP started in 1996. The purpose
of this testing effort was to further characterize spatial and temporal
distribution of ambient toxicity in the main stem and major tributaries
of the Sacramento River, and to determine the toxicants responsible
for observed toxicity. Three-species freshwater testing protocols
from the U.S. EPA were used in the performance of this work. These
bioassays measure survival, growth, and/or reproduction of sensitive
forms of the following test species: Ceriodaphnia dubia (water fleaprimary
consumer); Selanastrum capricornutum (algaeprimary producer); and
Pimephales promelas (fathead minnowsecondary consumer).
Samples
were taken from thirteen sites in the Sacramento River basin, ranging
from the Sacramento River at Freeport (near Sacramento) to the upper
Sacramento River (above Lake Shasta). Samples were collected approximately
monthly at most sites. Results of testing for the period August
1996 through July 1997 indicated the following:
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Fathead minnow impairment was observed at most sites, with the
exception of the Colusa Basin Drain and Sacramento Slough. Impairment
included acute and chronic mortality. Most frequent mortalities
were seen in higher quality, softer waters (McCloud River, Sacramento
River at Red Bluff). Toxicity identification evaluation (TIE)
work has indicated that a pathogen may be responsible for the
observed toxicity.
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Reduced algae growth was observed at only two sites (Pit
River and Arcade Creek). TIE work on Arcade Creek samples indicated
that the toxicant was a non-polar organic chemical.
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Ceriodaphnia mortality was observed at Arcade Creek and at the
Upper Sacramento River above Lake Shasta. Impaired Ceriodaphnia
reproduction was observed at all sites. TIE work indicated that
much of the observed Ceriodaphnia toxicity was linked to diazinon
and/or chlorpyrifos. Toxicity identification evaluation work in
the Upper Sacramento River linked observed toxicity to nickel.
Future
Direction
The
SRWP is continuing to move forward in the areas described above
and is also projecting activity in the following areas. These activities
are being developed and implemented by the SRWP Subcommittees, with
review and approval by the general stakeholder group.
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Monitoring Program: A plan for the second-year monitoring plan
is in place. The plan closely resembles the first-year plan, with
the following changes: addition of selected sites no longer covered
by the USGS NWQA program, expansion of the fish tissue monitoring
effort, expansion of tributary monitoring, and addition of chemical
analyses to a subset of the toxicity testing samples. Efforts
are underway by the Monitoring Subcommittee to develop a plan
for the third-year monitoring effort. The Subcommittee will consider
results from first-year monitoring before finalizing the third-year
plan.
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Public Outreach and Education: The Public Outreach and Education
Subcommittee has formed a communications workgroup comprised of
representatives from the following major stakeholder groups: California
Cattlemen's Association, Friends of the River, California Rice
Industry, Forest Products Association, Western Crop Protection
Association, and several others. The workgroup is developing a
public information effort to promote stewardship in the watershed,
by both industries and private citizens.
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Site-Specific Objectives: Examine possibility of developing site-specific
objectives for selected water quality parameters in the Sacramento
River Basin. Such enforceable objectives would be tailored to
local or regional conditions and would be scientifically defensible.
The objectives setting process would comply with federal and state
laws and regulations.
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Water Quality Management: The Toxics Subcommittee is considering
candidate constituents for selection for pilot efforts in water
quality management. The goal is to employ an interest-based, stakeholder-driven
approach in the development and implementation of measures to
address the selected constituents and to improve environmental
conditions and beneficial use attainment in the watershed.
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SRWP Institutional Structure: SRWP stakeholders will be evaluating
alternatives for the long-term structure of the program. The goal
is to select and implement a long-term structure for management,
administration, and funding which meets the interests of stakeholders.
Numerous options will be examined, drawing from experiences in
other similar groups across the country.
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