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Seasonal Usage of Off-Channel Habitats in the Entiat River by Juvenile Chinook Salmon Nicholas Albrecht and Tom Desgroseillier PIT Tag Workshop Skamania Lodge, WA January 27 th -29 th, 2015
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Integrated Status and Effectiveness Monitoring Program (ISEMP) Design monitoring programs to address multiple management objectives Assess the status of anadromous salmonid populations, their tributary habitat, restoration, and management actions – Status and Trend Monitoring – Intensively monitored watershed (IMW) Entiat River, WA Bridge Creek, John Day River, OR Lemhi River, ID – Evaluating benefits of habitat restoration
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The Entiat River Basin Originates from 11 glaciers and snowfields in the Cascade Mountains 69 km Drains 1,085km 2 Supports 8 salmonid species – Chinook Salmon (Oncorhynchus. tshawytscha) – Steelhead/Rainbow Trout (O. mykiss) – Sockeye (O. nerka) – Westslope cuttroat trout (O. clacki lewisi) – Coho Salmon (O. kisutch) – Mountain Whitefish (Prosopium williamsoni) – Bull Trout (Salvelinus confluentus) – Eastern Brook Trout (S. fontinalis)
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Goals/Objectives Investigate juvenile Chinook salmon usage of 5 off- channel habitats in the Entiat River utilizing Passive Integrated Transponders (PIT) tag technology and mark-recapture methods Size Density Survival Movement/Occupation of side channels
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Study Area
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Methods Sampling was done for 1 cohort of age-0 Chinook salmon from August 2013-April 2014 – Mainstem – Summer/Winter – Off-channel – Summer/Fall/Winter Population abundance was determined using mark-recapture methodoloy and estimated using Chapman-Petersen Method N = ((n 1 +1)(n 2 +1)/(m 2 +1 2 ))-1 Lengths and weights were taking on all fish All fish >50mm were PIT tagged
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Methods Barker Model 1 model with 5 groups (side channels) Model Selection Selection using evidence (weight) ratio that was derived from Quasi-likelihood Akaike Information Criterion adjusted for over-dispersion (QAIC) Goodness of fit was measured using bootstrapping Model was adjusted using c-hat
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Results Summer – 3D>SanRay>Wilson’s>Tyee=Harrison’s Fall – 3D=SanRay>Wilson’s=Harrison’s>Tyee Winter – Tyee=Wilson’s
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Summer – ANOVA: F-value=153.110 p=<.001 – VS3 was significantly different from 3D (p<0.001) and Tyee (p<0.001) in the summer – 3D>VS3>Tyee Winter – ANOVA: F-value=26.338 p=<.001 – Fork Length in VS3 was significant greater than Tyee (p<0.001)
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Summer – ANOVA: F-value=153.110 p=<.001 – VS1 was significantly different from Wilson’s (p=0.009), San Ray (p=0.003), and Harrison’s (p<0.001) – San Ray>VS1>Wilson’s>Harrison’s Winter – ANOVA: F-value=26.338 p=<.001 – Fork Length in VS1 was significant great than Wilson’s (p<0.001)
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Summer – 3D>SanRay>Wilson’s>Tyee=Harrison’s Fall – 3D>SanRay=Harrison’s=Wilson’s>Tyee Winter – Tyee=Wilson’s
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Summer – ANOVA: F-value=119.660 p=<.001 – VS3 was significantly different from 3D (p<0.001) and Tyee(p<0.001) – 3D>VS3>Tyee Winter – ANOVA: F-value=16.1978 p=<.001 – Weight in VS3 was significant greater than Tyee (p<0.001)
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Summer – ANOVA: F-value=119.660 p=<.001 – VS1 was significantly different from Wilson’s (p<0.001), and Harrison’s (p<0.001), but not San Ray (p=1.000) – San Ray=VS1>Wilson’s>Harrison’s Winter – ANOVA:F-value=16.197.338 p=<.001 – Weight in VS1 was significant greater than Wilson’s (p<0.001)
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SiteSlopeInterceptR2R2 Weight of 50mm Weight of 100mm 3D3.21-5.33.941.312.3 Tyee3.34-5.59.941.212.2 Wilson’s3.13-5.22.971.311.3 SanRay3.10-5.14.881.311.4 Harrison’s3.22-5.38.861.211.6
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SiteSlopeInterceptR2R2 Weight of 50mm Weight of 100mm 3D2.68-4.33.851.6910.82 Tyee3.11-5.18.951.2811.10 Wilson’s3.09-5.17.941.2410.67 SanRay3.28-5.51.921.1711.37 Harrison’s3.01-5.00.981.3511.00
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Density
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Survival
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Movement/Occupation 3D SummerFall
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Movement/Occupation Tyee SummerFall
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Movement/Occupation Wilson’s SummerFall
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Movement/Occupation San Ray SummerFall
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Movement/Occupation Harrison’s SummerFall
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Conclusions Length/Weight differences between side channels Difference in overwinter survival between side channels in VS3 and VS1 Fish densities varying by site and season Movement/Occupation of side channels varies between side channels in VS3 and VS1
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Future Directions Continue monitoring the current side channels Add additional side channels Conduct genetic analysis to determine the run-type of juvenile chinook utilizing the off- channel habitats Examine the effects of habitat
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Questions?
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