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Assess Current and Potential Salmonid Production in Rattlesnake Creek Associated with Restoration Efforts
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| Adult
salmon and steelhead have not had access to the White Salmon
River above river mile 3.2 since the completion of Condit Dam
in 1914. An assessment of rainbow trout populations serves as
a surrogate for evaluating factors that would limit salmon and
steelhead production if they are to be reintroduced in the watershed
above Condit Dam. |
The Problem
Rattlesnake Creek is a principal tributary to the White Salmon
River, Washington. Before the construction of Condit Dam in 1913
on the main-stem White Salmon River (at river mile 3.2), Rattlesnake
Creek was a productive stream for anadromous salmon, steelhead,
and coastal cutthroat trout. Condit Dam blocked access of anadromous
salmonids to Rattlesnake Creek, which enters the White Salmon River
at river mile 8.5. With the proposed removal or laddering of Condit
Dam scheduled for 2006, Rattlesnake Creek has high potential to
support reintroduced or naturally colonizing populations of salmon
and steelhead. Research on resident trout populations will serve
as a surrogate for an initial evaluation of limiting factors to
salmon and steelhead production in the watershed prior to major
habitat restoration activities and probable reintroduction of salmon
and steelhead. This project has been funded by Bonneville Power
Administration since FY2001 (Project number: 2001-025-00).
Objectives
Our research will characterize current habitat conditions, fish populations, water quality, fish diseases, and levels of stable isotopes of carbon and nitrogen. This baseline information will provide the necessary background to track changes and evaluate management actions associated with habitat restoration and potential removal or provision of fish passage above Condit Dam (river mile 3.2 of the White Salmon River, WA).
The two objectives of the project are: 1) Characterize stream and riparian habitat conditions in Rattlesnake Creek drainage, and 2) Determine the status of fish populations in the Rattlesnake Creek drainage.
Methodology
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| Personnel
from USGS-CRRL regularly measure stream flows at various sites
throughout the Rattlesnake Creek system. How flows respond to
rainfall events can have a large influence on the suitability
of a stream for fish production and persistence. |
We will conduct physical stream habitat surveys of Rattlesnake
Creek and its tributaries. These habitat surveys will quantify key
stream habitat components and indicators of aquatic health including:
1) large woody debris, 2) frequency and depth of pools, 3) substrate
composition, 4) stream gradient, 5) floodplain connectivity, and
6) riparian vegetation characteristics (e.g., species composition,
age structure, shading). Much of the stream lengths to be surveyed
will be on state and federally-managed lands. Private lands will
be surveyed when permission is secured from the landowners. Stream
discharge measurements will be taken in major tributaries and several
mainstem Rattlesnake Creek sites. These data will be used to characterize
temporal and spatial patterns of flow during late spring through
early fall (May--October) along the stream continuum.
The population density and biomass of resident salmonids in selected
portions of Rattlesnake Creek will be estimated, which will include
streams on state and federal lands and on as much of the privately-owned
lands as possible. These surveys will identify and measure dimensions
(e.g., length, width, and depth) of stream habitat units (e.g.,
pools, glides, riffles, etc.). Soon after these habitat surveys,
fish sampling will be conducted by snorkeling, electrofishing, or
a combination of both.
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| In
cooperation with the National Marine Fisheries Service, personnel
from USGS-CRRL have installed an instream PIT-tag detector in
the lower end of Rattlesnake Creek. To date, almost 2,000 rainbow
trout and cutthroat trout have been PIT tagged in the Rattlesnake
Creek and the mainstem White Salmon River. The detector runs
24 hours a day throughout the entire year, and it has yielded
much valuable information on the seasonal movement of juvenile
and adult fish. |
To document the distribution and abundance of individual fish species
within the watershed prior to restoration activities and the potential
removal or laddering of Condit Dam, we will largely use the data
collected during other aspects of the work. Where we are permitted
access, we will conduct additional sampling above barriers to determine
the distributional extent of resident fishes. In order to track
movements, growth, and other life history attributes of resident
salmonids, we will PIT tag most age-1 or older fish that we capture
during our stream surveys. We will continue to use and adjust our
remote PIT-tag detector that was established in 2001 with cooperation
with Earl Prentice, National Marine Fisheries Service. The ISO FDX-B,
134.2 400 kHz (12 mm) PIT tags that we use will be detectable at
Bonneville Dam in the event that these tagged fish migrate downstream
and exhibit an anadromous life history.
Because the possible removal or laddering of Condit Dam would allow
adult anadromous salmonids and other species access to Rattlesnake
Creek from the mainstem Columbia River, these fishes may introduce
new pathogens or parasites into the watershed. Knowledge of current
conditions will help managers anticipate and weigh possible risks
or threats to existing resident fish populations. We will obtain
fish for disease sampling using a longitudinal and tributary sampling
strategy. This will facilitate the development of a fish-health
baseline for areas that would be accessible and inaccessible (above
barriers) to anadromous salmonids in the future. Fish will be analyzed
by the U.S. Fish and Wildlife Service's Lower Columbia Fish Health
Center, which will provide a thorough disease profile as part of
the U. S. Fish and Wildlife Service's National Wild Fish Health
Survey.
A tissue sample (fin clip) from a subsample of salmonids captured during electrofishing
will be preserved (95% ethanol) for future genetic analyses
(an in-kind contribution will be sought to pay for this supplementary
genetics work). These data will serve as a genetic reference point
for rainbow trout and coastal cutthroat trout populations in the
watershed prior to the reestablishment of congeneric anadromous
salmonids.
Highlights and Key Findings
In FY2001, habitat and fish surveys were conducted in the mainstem
Rattlesnake Creek and its tributary, Indian Creek. These study areas
were sampled for salmonids and other fish species by backpack electroshocking
and snorkeling within a stratified systematic sampling design. Both
rainbow trout and cutthroat trout were found in these streams along
with longnose dace, shorthead sculpin, and brook lamprey. Stream
discharge measurements were taken at semi-weekly or bi-monthly intervals
at four samplings sites from June through October. Habitat surveys
were conducted to determine frequency of pools and woody debris
pieces, as well as stream width, gradient, and riparian shade.
Where Are We Headed In 2003
We will continue to characterize stream and riparian habitat conditions,
and continue to determine the status of fish populations in the
Rattlesnake Creek drainage. By partnering with the U.S. Forest Service
and the Confederated Tribes and Bands of the Yakama Indian Nation,
we will explore the importance of Rattlesnake Creek to the White
Salmon River rainbow trout population. By a combination of PIT-tagging
and radio tagging rainbow trout, we will let the fish tell us the
degree of connectivity between Rattlesnake Creek and the mainstem
White Salmon River.
Project Contact
Patrick J. Connolly
U.S. Geological Survey
Western Fisheries Research Center
Columbia River Research Laboratory
5501-A Cook-Underwood Rd.
Cook, WA 98605-9717
Email: patrick_connolly@usgs.gov
Phone: 509-538-2299 x269
Fax: 509-538-2843
Publications
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