UPPER WILLAMETTE RIVER SPRING CHINOOK ABUNDANCE, DISTRIBUTION AND SURVIVAL: McKenzie Addendum

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UPPER WILLAMETTE RIVER SPRING CHINOOK ABUNDANCE, DISTRIBUTION AND SURVIVAL: McKenzie Addendum Cameron Sharpe Oregon Department of Fish and Wildlife Willamette Science Review February 4-6, 2014

Willamette Biological Opinion Hatchery Research, Monitoring, and Evaluation

Acknowledgments Funding: US Army Corps of Engineers and Federal Sport Fish Restoration Fund Administrative/ Technical Support: Tom Friesen Marc Johnson Luke Whitman Brian Cannon Field Staff: Paul Olmsted Dave Hewlett Sara Akins Brian Franklin Justin Huff Kevin Stertz Chris Abbes Amy Anderson Riley Newman Sara Taylor Dan Coffman Bart DeBow Mike Hogansen Reed Fischer Aaron Funke JD Hansen Chris Mayes Tim Plawman Gordon Rose Keenan Smith Kyle Pritchard David Metz Hatchery Managers: Greg Grenbemer Brett Boyd Kurt Kremers Dan Peck

Hatchery RME Activities Monitoring hatchery operations and conducting research focused on hatchery programs Spawning ground surveys (upstream & downstream of dams), Distribution & abundance of redds, carcass sampling, proportion hatcheryorigin spawners (PHOS) prespawn mortality, straying, diversity

VSP Monitoring Guidelines (Crawford and Rumsey 2011) Adult Spawner Abundance and Productivity Spatial Distribution Species Diversity

Methods Carcass Sampling Redd Surveys

REDDS AUGUST: SPAWNING COMMENCES DEADS PROCESSABLE CARCASSES/REACH SEPTEMBER: REDDS ACCUMULATE, PEAK SPAWNING LATE CLIPPED UNCLIPPED OTOLITHS OCTOBER: SPAWNING ENDS, PEAK COUNT OBTAINED THERMAL MARKS NO THERMAL MARKS SPAWNER ABUNDANCE (N T ) = PEAK COUNT/REACH * 2.5 HATCHERY- ORIGIN (H) NATURAL- ORIGIN (W) N W = N * (1 phos) N H = N T * phos phos = H/(H + W)

September 2013 Precip. Percent of Normal Redds under-counted Spawned carcasses under-sampled

Implications Peak Redd Counts May Be Biased LOW More reliance on relative abundance and distribution PSM Estimates May Be Biased HIGH High estimates are suspect Low estimates acceptable Assume run composition (phos, size, age, mark rates) are unbiased

Below Leaburg Dam N: 75 redds d: 7.8 redd/km PSM: 24% PHOS: 84% Leaburg Dam to Cougar Dam N: 146 redds d: 4.1 redd/km PSM: 3% PHOS: 35% McKenzie Above SF McKenzie N: 349 redds d: 4.7 redd/km PSM: 3% PHOS: 7% SF McKenzie Above Cougar Dam N: 146 redds d: 4.1 redd/km PSM: 25% PHOS: 79%

Spawner Abundance 2000 1800 1600 1400 1200 1000 800 600 400 200 natural origin spawners Below Leaburg hatchery origin spawners Below Leaburg Wild Prelim 2013 Hatch Prelim 2013 phos 1.0 0.9 0.8 0.7 0.6 0.5 0.4 0.3 0.2 0.1 phos 0 0.0 2000 2002 2004 2006 2008 2010 2012 2014 Run Year

Spawner Abundance 6000 5000 4000 3000 2000 1000 0 W Spawners abv lbg from redd exp H Spawners abv lbg from redd exp Wild Prelim 2013 Hatch Prelim 2013 phos 2000 2002 2004 2006 2008 2010 2012 2014 Run Year 0.50 0.45 0.40 0.35 0.30 0.25 0.20 0.15 0.10 0.05 0.00 phos

Net movement of fish a counted on video at Leaburg Dam on the McKenzie River in 2013. Month Unmarked Steelhead Hatchery Summer Steelhead Unclipped ("Wild") Chinook Hatchery Chinook Lamprey January 0 0 0 0 0 February -1 0 0 0 0 March 1 2 1 0 0 April 1 25 1 0 0 May 5 126 111 6 0 June 26 288 652 108 3 July 20 191 318 47 19 August 1 50 63 14 7 September 3 27 86 86 2 October 1 34 4 0 1 November 0 0 0 0 0 December 0 0 0 0 0 Total 2013 57 743 1,236 261 32

2013 Redds & Carcasses ITM Section Peak Redd Count Total Carcasses Processed Below Leaburg 75 61 Leaburg to Cougar 146 64 Above South Fork McKenzie South Fork McKenzie Above Cougar 349 66 146 32 Redd Distribution vs Carcass Distribution G (adj) 48.36 df 2 P-value Error report 3.14E-11 No errors encountered G(crit) 5.99

ITM Section Count Clipped Count Unclipped % Thermally Marked Wild Est Hatch Est Below Leaburg Leaburg to Cougar Above South Fork McKenzie South Fork McKenzie Above Cougar 49 12 0.19 10 51 20 44 0.05 42 22 1 65 0.05 62 4 25 7 0.05 7 25 5 y Avg Thermal Mark Rate Year Abv Below Leaburg Leaburg 2008 0.03 0.06 2009 0.05 0.18 2010 0.07 0.33 2011 0.04 0.10 2012 0.07 0.27 MEAN 0.05 0.19

ITM Section Wild Est Hatch Est Unweighted phos Below Leaburg 10 51 84.1% Leaburg to Cougar 42 22 34.8% Above South Fork McKenzie South Fork McKenzie Above Cougar 62 4 6.6% 7 25 79.3%

ITM Section Peak Redd Count Unweighted phos Above Leaburg without Above Cougar Basinwide Below Leaburg 75 84.1% Leaburg to Cougar 146 34.8% 14.9% 39.4% Above South Fork McKenzie 349 6.6% South Fork McKenzie Above Cougar 146 79.3%

60 50 40 Count 30 20 10 0 60 70 80 90 100 Fork Length (mm)

50 45 40 35 30 Count 25 20 15 10 5 0 3 4 5 Total Age

Age CWT Age Scale Age 3 1 0 4 47 44 5 7 10 6 0 1

Age Validation Age CWT Age Scale Age 3 1 0 4 47 44 5 7 10 6 0 1

CWT Recovery Rates (BY1995-2009) CWT Recovery Rate 1.2% 1.0% 0.8% 0.6% 0.4% 0.2% 0.0% November February March Release Time BY 1995-2009

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