Little is known about use of the Columbia River by bull trout Salvelinus confluentus from the
Walla Walla Basin. Mainstem Snake and Columbia River dams have the potential to impact
both the connectivity between bull trout Core Areas (metapopulations), and the connectivity
within migratory corridors. The need for research and monitoring of bull trout use of the
Columbia and Snake rivers is identified in the U.S. Fish and Wildlife Service Biological
Opinion. From April 2005 through December 2009, use of the Columbia River by Walla Walla
Basin bull trout was investigated by operating a Passive Integrated Transponder (PIT) detection
array at Oasis Road Bridge (ORB) near the mouth of the Walla Walla River to determine bull
trout abundance and describe the migration timing between the Walla Walla and Columbia
rivers. A quantitative estimate of the number of migratory Walla Walla Basin bull trout that
moved into the Columbia River over the duration of this study was developed by utilizing
empirical data consisting of monthly array detections in combination with physical detection
efficiencies and annual estimates of the proportion of the population that was tagged based on
hook and line sampling. Migration timing periodicity was described by examining detections at
the ORB detection array, observations from a screw trap operated near the mouth of the Walla
Walla River, and detections at mainstem dams. Migration timing was also examined for
temporal patterns of activity, including peak migration periods, using abundance estimates. Data
were insufficient to estimate migratory abundance during 2005 and 2006. We estimate a total of
192 bull trout emigrated from the Walla Walla Basin to the Columbia River from November
2007 through December 2009. Over the duration of the study, only one bull trout was detected
returning to the Walla Walla River from the Columbia River. We did not attempt to make any
estimates of the total number of returning adults for the single detection in June 2009. The
timing of migratory bull trout emigration from the Walla Walla River to the Columbia River
varied from year to year, but overall, occurred from October through May, peaking between
November and February. Variation in streamflow patterns across migration seasons appears to
influence emigration timing to a greater extent than changing water temperatures. The single
detection of a returning bull trout in June was similar to upstream migration timing observations
at other PIT detection arrays throughout the Walla Walla Basin, and other historic observations
of upstream migrants. Four Walla Walla Basin bull trout were detected at mainstem Columbia
River dams over the duration of this study. Detections in the juvenile bypass systems at John
Day and McNary dams indicated two of these bull trout were moving downstream. Detections in
the adult fish ladders at McNary and Priest Rapids dams indicated two of these bull trout were
moving upstream. Walla Walla Basin connectivity with the mainstem Columbia River, and
connectivity within the Columbia River migratory corridor is required to maintain genetic
diversity of the Core Area metapopulations in the Columbia River Distinct Population Segment,
and for re-colonization of areas where local populations have been extirpated by natural
stochastic events or impacts from human-related activities. Future work should include
monitoring efforts in the mainstem Columbia River to provide a more detailed understanding of
the temporal and spatial aspects of mainstem habitat use and migration by Walla Walla Basin
bull trout, and how they interact with the dams and reservoirs of the Federal Columbia River
Power System.
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