Salmonid Population and Life History Research in Tributary Stream and River Habitats and Response to Dam Removal
Juvenile Steelhead to be Tagged with a PIT Tag
Juvenile anadromous salmonids all spend some portion of their lives in freshwater. This time may vary from days to years depending upon species and run. Spring Chinook Salmon and Coho salmon generally spend one year in freshwater and Steelhead may spend up to five years in freshwater prior to beginning their journey to sea. Several projects at WFRC – CRRL are investigating populations, life-histories, habitat, and potential limiting factors on the freshwater rearing juvenile salmonids. Much data on salmonid ecology and life-histories is gathered through tagging fish with Passive Integrated Transponder (PIT) tags. Instream PIT tag detection systems are a tool we have employed in many watersheds throughout the west and continue to do so in several local watersheds including the Wind River and Rock Creek, WA.
A project in the Wind River, WA is focusing on steelhead populations, life histories, habitat, and limiting factors as part of a multi-agency effort to restore steelhead populations in the Wind River. These efforts are contributing to a greater understanding of the diversity of Steelhead life-histories and the factors driving different life-history expressions in a wild Steelhead population. Of interest are migratory parr and their fates compared to headwater rearing parr that do not migrate until smolting. Efforts to date have demonstrated that parr Steelhead migrate from headwater rearing areas as young as age-0 and do so throughout the year.
A portion of the Wind River work has focused on interaction between juvenile Steelhead an introduced run of hatchery spring Chinook salmon, which has demonstrated little effect of hatchery Chinook spawning on wild Steelhead populations. Our sampling efforts provide data to inform life-cycle modeling, estimate life-stage specific survival, and identify potential population bottlenecks. Additionally, these data are contributing to evaluation of the Steelhead response to the removal of Hemlock Dam from Trout Creek, which occurred in 2009.
An ongoing project is juvenile salmonid monitoring in the White Salmon River following removal of Condit Dam in 2011. Condit Dam had completely blocked the White Salmon for nearly 100 years. Our goals are to assess smolt production from upstream of rkm 2.3, juvenile salmonid distribution in the watershed, and juvenile salmonid abundance at sites in Buck and Rattlesnake Creeks as natural recolonization occurs. Species recolonizing the White Salmon include Steelhead, Coho salmon, and both spring and fall Chinook salmon. Data collected on populations, behavior, and genetics will help evaluate dam removal as a restoration and conservation strategy, assess the efficacy of a natural recolonization strategy for anadromous salmonids, and inform managers of the status of ESA listed salmonid stocks.
Below are publications associated with this project.
Juvenile salmonid monitoring following removal of Condit Dam in the White Salmon River Watershed, Washington, 2017
Juvenile salmonid monitoring in the White Salmon River, Washington, post-Condit Dam removal, 2016
Wind River subbasin restoration: Annual report of U.S. Geological Survey activities January 2014 through December 2014
Biotic and abiotic influences on abundance and distribution of nonnative Chinook salmon and native ESA-listed steelhead in the Wind River, Washington
Wind River subbasin restoration: U.S. Geological Survey annual report November 2012 through December 2013
Distribution and movement of Big Spring spinedace (Lepidomeda mollispinis pratensis) in Condor Canyon, Meadow Valley Wash, Nevada
Hood River PIT-tag interrogation system efficiency study. Annual report of U.S. Geological Survey activities: November 2010-October 2011
Big Spring spinedace and associated fish populations and habitat conditions in Condor Canyon, Meadow Valley Wash, Nevada
Wild Steelhead and introduced spring Chinook Salmon in the Wind River, Washington: Overlapping populations and interactions
Measuring the performance of two stationary interrogation systems for detecting downstream and upstream movement of PIT-tagged salmonids
Wind River Watershed Restoration: Annual report April 2006 to March 2007
Wind River Watershed Restoration: Annual Report April 2005 - March 2006
Partners associated with this project include the Mid-Columbia Fisheries Enhancement Group, Washington Department of Fish and Wildlife, U.S. Forest Service, U.S. Fish and Wildlife Service, and the Yakama Nation Fisheries.
Juvenile anadromous salmonids all spend some portion of their lives in freshwater. This time may vary from days to years depending upon species and run. Spring Chinook Salmon and Coho salmon generally spend one year in freshwater and Steelhead may spend up to five years in freshwater prior to beginning their journey to sea. Several projects at WFRC – CRRL are investigating populations, life-histories, habitat, and potential limiting factors on the freshwater rearing juvenile salmonids. Much data on salmonid ecology and life-histories is gathered through tagging fish with Passive Integrated Transponder (PIT) tags. Instream PIT tag detection systems are a tool we have employed in many watersheds throughout the west and continue to do so in several local watersheds including the Wind River and Rock Creek, WA.
A project in the Wind River, WA is focusing on steelhead populations, life histories, habitat, and limiting factors as part of a multi-agency effort to restore steelhead populations in the Wind River. These efforts are contributing to a greater understanding of the diversity of Steelhead life-histories and the factors driving different life-history expressions in a wild Steelhead population. Of interest are migratory parr and their fates compared to headwater rearing parr that do not migrate until smolting. Efforts to date have demonstrated that parr Steelhead migrate from headwater rearing areas as young as age-0 and do so throughout the year.
A portion of the Wind River work has focused on interaction between juvenile Steelhead an introduced run of hatchery spring Chinook salmon, which has demonstrated little effect of hatchery Chinook spawning on wild Steelhead populations. Our sampling efforts provide data to inform life-cycle modeling, estimate life-stage specific survival, and identify potential population bottlenecks. Additionally, these data are contributing to evaluation of the Steelhead response to the removal of Hemlock Dam from Trout Creek, which occurred in 2009.
An ongoing project is juvenile salmonid monitoring in the White Salmon River following removal of Condit Dam in 2011. Condit Dam had completely blocked the White Salmon for nearly 100 years. Our goals are to assess smolt production from upstream of rkm 2.3, juvenile salmonid distribution in the watershed, and juvenile salmonid abundance at sites in Buck and Rattlesnake Creeks as natural recolonization occurs. Species recolonizing the White Salmon include Steelhead, Coho salmon, and both spring and fall Chinook salmon. Data collected on populations, behavior, and genetics will help evaluate dam removal as a restoration and conservation strategy, assess the efficacy of a natural recolonization strategy for anadromous salmonids, and inform managers of the status of ESA listed salmonid stocks.
Below are publications associated with this project.
Juvenile salmonid monitoring following removal of Condit Dam in the White Salmon River Watershed, Washington, 2017
Juvenile salmonid monitoring in the White Salmon River, Washington, post-Condit Dam removal, 2016
Wind River subbasin restoration: Annual report of U.S. Geological Survey activities January 2014 through December 2014
Biotic and abiotic influences on abundance and distribution of nonnative Chinook salmon and native ESA-listed steelhead in the Wind River, Washington
Wind River subbasin restoration: U.S. Geological Survey annual report November 2012 through December 2013
Distribution and movement of Big Spring spinedace (Lepidomeda mollispinis pratensis) in Condor Canyon, Meadow Valley Wash, Nevada
Hood River PIT-tag interrogation system efficiency study. Annual report of U.S. Geological Survey activities: November 2010-October 2011
Big Spring spinedace and associated fish populations and habitat conditions in Condor Canyon, Meadow Valley Wash, Nevada
Wild Steelhead and introduced spring Chinook Salmon in the Wind River, Washington: Overlapping populations and interactions
Measuring the performance of two stationary interrogation systems for detecting downstream and upstream movement of PIT-tagged salmonids
Wind River Watershed Restoration: Annual report April 2006 to March 2007
Wind River Watershed Restoration: Annual Report April 2005 - March 2006
Partners associated with this project include the Mid-Columbia Fisheries Enhancement Group, Washington Department of Fish and Wildlife, U.S. Forest Service, U.S. Fish and Wildlife Service, and the Yakama Nation Fisheries.