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Survival of adult spring/summer Chinook salmon (Oncorhynchus tshawytscha) through the estuary and lower Columbia River amid a rapidly changing predator population A. Michelle Wargo Rub, Ben Sandford, Don Van Doornik, David Teel, Matthew Nesbit, Samuel Rambo, Jesse Lamb, Louis Tullos, Kinsey Frick, April Cameron, Nicholas Som, Mark Henderson, Mark Sorel, David Huff and Rich Zabel NOAA Fisheries Northwest Fisheries Science Center (NWFSC)

The primary goal of this study is to provide estimates of survival and run timing through the estuary and lower CR for spring/summer Chinook salmon returning to the Middle & Upper Columbia & Snake Rivers There is concern that pinnipeds entering the CR during spring is impacting adult salmon through predation 234 RKM UCR ESA Listed Photo credit: Washington Department of Fish and Wildlife March 2015; 6k harbor seals (top) & 2k sea lions (bottom) Study Area MCR SR Photo credit: Washington Department of Fish and Wildlife

Commercial tangle net crew hauling in a Chinook salmon Fish are captured by CR commercial fishermen, tagged by NOAA Fisheries research biologists, and released. Greater than 2500 adult salmon have been PIT- tagged for this study since 2010.

NOAA & ODFW began tracking fish and pinnipeds using RT in 2016

Weighted Mean Survival for Interior CR adults (FL 56 cm) Year Adult Chinook salmon (N) Range of sampling dates Baseline Survival (95% CI) *Preliminary estimates and assume 7% harvest Baseline Mortality Potential Mortality due to harvest and handling Unexplained mortality 2010 172 4/14-5/11.74 (.68-.80) 0.26 0.15 0.11 2011 381 4/1-5/16.73 (.69-.77) 0.27 0.14 0.13 2012 372 3/23-5/31.69 (.64-.75) 0.31 0.16 0.15 2013 73 4/19-6/14.60 (.47-.74) 0.40 0.12 0.28 2014 297 3/20-5/13.46 (.38-.53) 0.54 0.11 0.43 2015 205 3/19-5/8.52 (.42-.61) 0.48 0.11 0.37 2016* 70 3/28-5/23.70 (.58-.82) 0.30 0.16 0.14 2017* 89 3/21-5/22.62 (.50-.74) 0.38 0.14 0.24

Upriver spring/summer Chinook salmon mortalities year Total CR spring/summer Chinook salmon returns (N) Upriver spring/summer Chinook salmon returns (N) Number of upriver fish mortalities (95% CI) 2010 468,536 315,345 (.67) 34,688 (9,460-59,916) 2011 323,099 221,158 (.68) 28,751 (2,212-33,174) 2012 297,034 203,090 (.68) 30,464 (18,278-40,618) 2013 192,881 123,136 (.64) 34,478 (13,545-54,180) 2014 313,491 242,635 (.77) 104,333 (82,496-126,170) 2015 416,731 288,994 (.69) 106,928 (75,138-138,717) 2016 137,215* 19,210 (2,744-37,048) 2017 101,008** 24,242 (10,101-39,393) *Upriver return to Bonneville Dam as of 5/31/17 **Upriver return to Bonneville Dam as of 6/11/17

Radio Telemetry Results 2016 50% 13% 10% 13% 18% California Sea Lion Presence N=30 Chinook Salmon Mortality N=80 33% 3% 48% 7% 3%

Radio Telemetry Results 2017 73% 7% 15% 0% California Sea Lion Presence N=30 Chinook Salmon Mortality N=78 50% 0% 10% 25% 3% 0%

Linear Mixed Effects Modelling Random effect: Week of tagging nested within year with autoregressive component Fixed effects: Clip status Exposure to California Sea Lions based on EMB abundance during the week fish were tagged Abundance of Shad in the estuary during the week fish were tagged Note: Annual Eulachon abundance is highly correlated (=.83) with annual CSL abundance *The area under the ROC was.70 indicating the model is good with respect to being able to predict survival

Model response curves: Survival Probability

What have we learned? We have identified significant mortality that is unexplained by harvest and handling for upriver spring/summer Chinook salmon This mortality appeared to peak during 2014 and 2015 at approximately 100k fish. Pinniped predation is likely the primary source of mortality but not all animals are equal with respect to the impact they are having on returning fish Additional covariates potentially influencing survival include the abundance of shad, and clip status, and the abundance of eulachon Stay tuned.. Up close study of tailrace survival Population level survival and behavior as we summarize results using parentage-based genetics

Acknowledgements: Susan Hinton, George McCabe, Paul Bentley, and Bob Emmett of NOAA Fisheries Pt. Adams Research Station, Jim Simonson and crew of NOAA Fisheries Pasco Research Station, Laurie Weitkamp of NOAA Fisheries NWFSC, Newport Research Station, David Kuligowski of NOAA Fisheries NWFSC, Manchester Research Station, John Hess, Doug Hatch & Ryan Brandstetter of CRITFC, Jason Romine and Mike Parsley of USGS, Chris Kern and Geoffrey Whisler, Matt Tennis, Bryan Wright, Robin Brown of ODFW, Steve Jeffries of WDFW, Matt Campbell of IDF&G, Brian, Frank, & Stephanie Tarabochia, and Dan Marvin of Astoria, OR, Sean Hayes of NOAA Fisheries SWFSC, Kane Cunningham & Colleen Reichmuth of the Institute of Marine Sciences, Long Marine Laboratory, UCSC, NOAA Near Term Priority (2010 & 2011) and NOAA Fisheries Cooperative Research (2012, 2013, & 2014), Albert Little, Wyatt Wullger, Ben Rudolph, & Cody May of Ocean Associates, Dave Caton & Lila Charlton of PSMFC

% Fish Survival Numbers of sea lions 1.60 1.40 1.20 2010 2011 2012 2013 2014 2015 2000 1800 1600 1400 1.00 Survival trend 2010-2012 (upper curve) 1200 0.80 0.60 0.40 0.20 Survival trend 2013-2015 (lower curve) 1000 800 600 400 200 0.00 0 3/11 3/21 3/31 4/10 4/20 4/30 5/10 5/20 5/30 6/9 6/19 Figure 1. Trends in Survival for PIT-tagged adult Chinook salmon tagged from 2010-2012 and from 2013-2015 (dashed and solid lines) and the corresponding number of sea lions observed at haul out sites (vertical bars) near Astoria, Oregon (rm 16).