UPPER WILLAMETTE RIVER SPRING CHINOOK ABUNDANCE, DISTRIBUTION AND SURVIVAL: McKenzie Addendum
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1 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
2 Willamette Biological Opinion Hatchery Research, Monitoring, and Evaluation
3 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
4 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
5 VSP Monitoring Guidelines (Crawford and Rumsey 2011) Adult Spawner Abundance and Productivity Spatial Distribution Species Diversity
6 Methods Carcass Sampling Redd Surveys
7 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)
8 September 2013 Precip. Percent of Normal Redds under-counted Spawned carcasses under-sampled
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12 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
13 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%
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18 Spawner Abundance natural origin spawners Below Leaburg hatchery origin spawners Below Leaburg Wild Prelim 2013 Hatch Prelim 2013 phos phos Run Year
19 Spawner Abundance W Spawners abv lbg from redd exp H Spawners abv lbg from redd exp Wild Prelim 2013 Hatch Prelim 2013 phos Run Year phos
20 Net movement of fish a counted on video at Leaburg Dam on the McKenzie River in Month Unmarked Steelhead Hatchery Summer Steelhead Unclipped ("Wild") Chinook Hatchery Chinook Lamprey January February March April May June July August September October November December Total ,
21 2013 Redds & Carcasses ITM Section Peak Redd Count Total Carcasses Processed Below Leaburg Leaburg to Cougar Above South Fork McKenzie South Fork McKenzie Above Cougar Redd Distribution vs Carcass Distribution G (adj) df 2 P-value Error report 3.14E-11 No errors encountered G(crit) 5.99
22 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 y Avg Thermal Mark Rate Year Abv Below Leaburg Leaburg MEAN
23 ITM Section Wild Est Hatch Est Unweighted phos Below Leaburg % Leaburg to Cougar % Above South Fork McKenzie South Fork McKenzie Above Cougar % %
24 ITM Section Peak Redd Count Unweighted phos Above Leaburg without Above Cougar Basinwide Below Leaburg % Leaburg to Cougar % 14.9% 39.4% Above South Fork McKenzie % South Fork McKenzie Above Cougar %
25 Count Fork Length (mm)
26 Count Total Age
27 Age CWT Age Scale Age
28 Age Validation Age CWT Age Scale Age
29 CWT Recovery Rates (BY ) CWT Recovery Rate 1.2% 1.0% 0.8% 0.6% 0.4% 0.2% 0.0% November February March Release Time BY
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31 Questions?
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