Committee chair: Christian Torgersen
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1 Jeremy Cram 1, Christian Torgersen 2, Ryan Klett 1, George Pess 3, Andrew Dittman 3, Darran May 3 Committee chair: Christian Torgersen 1. University of Washington, School of Forest Resources, Seattle, WA USA 2. U.S. Geological Survey, Forest and Rangeland Ecosystem Science Center, Cascadia Field Station, University of Washington, College of Forest Resources, Seattle, WA USA 3. NOAA Northwest Fisheries Science Center, 2725 Montlake Boulevard East, Seattle, Washington 98112, USA
2 Capable of precise navigation at multiple spatial scales Open ocean to freshwater Within freshwater system Site of incubation Homing confers an evolutionary advantage, just as migration does Allows for local adaptation Improves likelihood of successful reproduction Evident in many species mountain whitefish, northern pikeminnow, largescale suckers
3 Evolutionary mechanism to avoid disturbance Mt. St. Helens Flooding Colonize newly accessible habitats Glacier Bay, AK Upper Cedar River, WA Find better spawning habitat?
4 Jack Creek Easton Clark Flat Roza Dam
5 Hatcheries are controversial and expensive Each adult fish costs $14 - $530 (WA Ecology 2002) Create jobs and fishing opportunity Genetic and ecological risks to wild fish Integrated practices rely on habitat, which may be fully utilized by wild fish
6 Extensive survey September 2007 Channel type (1,2,3) Unit type (PO,GP,GR, RI) Channel width Depth Substrate Cover Wood Fish abundance 125 m Survey summary 140 km mainstem 20 km side channel
7 Carcass and redd surveys ( ) Surveys conducted by Yakama Nation and NOAA Fisheries GPS location Origin (CWT) Gender Age class Length 2007 Redds 125 m
8 How does available habitat compare near hatchery facilities on the Yakima River? If a fish strays from its acclimation area, is it due to habitat differences?
9 Density redds/km) SUM_REDDNU (1km) SUM_REDDNU (2km) SUM_REDDNU (4km) 1 km 2 km 4 km % Cover COVV_PERC + COVW_PERC (1km) COVV_PERC + COVW_PERC (2km) COVV_PERC + COVW_PERC (4km) Mean wet width (m) WET_WIDTH (1km) WET_WIDTH (2km) Distance upstream (km) WET_WIDTH (4km)
10 Clark Flat Easton Deep Shallow Downstream Upstream
11 Clark Flat Easton
12 (14 %) (19 %)
13 Clark Flat (31 %) Easton (38 %)
14 Environmental conditions vary throughout the system, including near each hatchery facility Keefer et al. (2008) showed that spring Chinook wander before spawning
15 Density (carcasses/km) Female carcasses 2007 Clark Flat Teanaway River Hatchery Cle Elum River Easton Hatchery Wild Distance upstream (km)
16 Redds 2007 Cle Elum River Density (redds/km) Clark Flat Teanaway River Hatchery Easton Distance upstream (km)
17
18 100 1 km r 2 = Redds/km Principal component 1 score
19 200 8 km r 2 = Redds/km Principal component 1 score
20 Habitat near hatchery facilities is different across spatial scales Spawning distribution is nearly identical for wild- and hatchery-origin females Supplementation fish frequently spawn away from acclimation areas in more suitable habitat
21 Logistics and GIS: Darran May, Hiroo Imaki, Ethan Welty, John Vaccaro, Patricia Haggerty Fieldwork: Tanya Cram, James Chu, Ethan Welty Housing and support: Everyone at the Cle Elum supplementation and research facility Funding: NOAA BiOP, The Water Center Photography: Ethan Welty Aerial photos: NAIP Allyson Jason
22 Redds Wild females Hatchery females 10 8 Redds/km Carcasses/km Distance upstream (km)
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