Alsea Steelhead Acoustic Tagging Project. ODFW -Salmonid Life Cycle Monitoring Project Alsea Steelhead Acoustic Tagging Project EPA – Estuarine Habitat.

Slides:



Advertisements
Similar presentations
Natural Reproductive Success and Demographic Effects of Hatchery-Origin Steelhead in Abernathy Creek, Washington Abernathy Fish Technology Center U.S.
Advertisements

Salmonid Natural Production Monitoring & Evaluation Project Confederated Tribes of the Umatilla Indian Reservation BPA Project #
Investigate the Life History of Spring Chinook Salmon and Summer Steelhead in the Grande Ronde River Basin Project Brian Jonasson Oregon Department.
Annual Stock Assessment – Coded Wire Tag Program (ODFW & WDFW) BPA Project Numbers: and
Survival Estimates for the Passage of Juvenile Salmonids Through Dams and Reservoirs of the Lower Snake and Columbia Rivers (Project ) CBFWA March.
SELECT AREA FISHERY EVALUATION BPA Project # CEDC, ODFW, WDFW.
Investigate Re-establishing Anadromous Fish Populations Above Man-made Barriers Oregon Department of Fish and Wildlife Willamette Basin.
Evaluation of Juvenile Salmonid Outmigration and Survival in the Lower Umatilla River Project No Tara White, Shannon Jewett, Josh Hanson,
Evaluate juvenile salmon residence in the Columbia River Plume using micro-acoustic transmitters John Ferguson, et al. Riverine Ecology Program NWFSC,
Frank Leonetti, Snohomish County
Okanagan Sockeye Reintroduction program 18 October, 2012 Portland, Oregon Howie Wright.
Rebecca A. Buchanan Columbia Basin Research School of Aquatic and Fishery Sciences University of Washington Seattle, WA INVESTIGATING MIGRATORY PROCESSES.
Looking for Pieces of the Puzzle: LIFE HISTORY OF SPRING CHINOOK IN THE WILLAMETTE BASIN Kirk Schroeder Brian Cannon Luke Whitman Paul Olmsted Oregon Department.
Overview of Current Production Programs Across the Columbia River Basin.
Assessing the use of PIT Tags as a Tool to Monitor Adult Chinook Salmon Returns to Idaho John Cassinelli Regional Fisheries Biologist Idaho Department.
Apparent over-winter survival of juvenile coho in three tributaries to the lower Columbia River Trevor Johnson, Mara Zimmerman, Matthew Sturza, Patrick.
Kathryn Kostow Oregon Department of Fish and Wildlife A Demonstration of Modified Selection Pressures in a Steelhead Hatchery Program on the Hood River,
Management strategies for balancing hatchery functions with natural fish protections Brad Cavallo.
Environmental Factors Affecting Salmon Production Washington Department of Fish & Wildlife Science Division Dave Seiler.
Development of the Lower Snake River Compensation Plan: A Brief History Scott Marshall LSRCP Program Administrator U.S. Fish & Wildlife Service.
Tucannon Endemic Steelhead – An Integrated Program picture.
Fecundity Management Strategies. Why Talk About This? As managers, we utilize various methods in managing broodstock collection – we never want to be.
Implementation of the Biological Opinion for Russian River Water Supply, Flood Control Operations & Channel Maintenance National Marine Fisheries Service.
Variation in Straying Patterns and Rates of Snake River Hatchery Steelhead Stocks in the Deschutes River Basin, Oregon Richard W. Carmichael and Tim Hoffnagle.
Columbia River salmon : Who (or what) will save them? John Williams Klarälven meeting in Karlstad 9 May 2011.
Combining PIT Tags with Scale Reading to Better Understand the Life History of Snake River Fall Chinook Salmon Douglas Marsh and William Muir - NOAA Fisheries.
Emigration behavior of resident and anadromous juvenile O. mykiss: exploring the interaction among genetics, physiology and habitat Sean Hayes, Chad Hanson,
Inbreeding and inbreeding depression in hatchery steelhead K Naish, TR Seamons, M Dauer, T Quinn, L Hauser University of Washington School of Aquatic and.
Monitoring Estuarine Survival of Steelhead (Oncorhynchus mykiss) Smolts in the Nehalem and Alsea Basins, Oregon Using Acoustic Telemetry Jeremy Romer,
Survival of Migrating Salmonid Smolts in the Snake and Lower Columbia Rivers, 2009 Technical Management TeamDecember 11, 2009 Lessons Learned 2009 Bill.
Documenting O. mykiss life histories in the White Salmon River prior to the reintroduction of anadromous fish above Condit Dam. Brady Allen and Patrick.
Monitor and Evaluate Salmonid Production in the Asotin Creek Subbasin - LSRCP (ID #200116)
Role of Tidal Saltwater Habitats for Juvenile Salmonids (Myths vs Reality in the Columbia River Estuary) Ed Casillas NWFSC, Seattle, WA (Contributors –
Growth Trajectories of Wild California Steelhead Parr David Swank 1,2, Will Satterthwaite 1, Michael Beakes 1, Susan Sogard 2, Marc Mangel 1, Rob Titus.
Steelhead Stock Status Review and ESA Oregon Rhine Messmer ODFW District Staff Oregon Department of Fish and Wildlife Pacific Coast Steelhead Management.
Life History of Western Washington Winter Steelhead, a 30 Year Perspective Hal Michael Washington Department of Fish and Wildlife
Grande Ronde Basin Spring Chinook: Relative Reproductive Success in Captive Chinook Salmon Melissa Baird 1, Ewann Berntson 1, Timothy Hoffnagle 2, Steve.
Management & Recovery Implications Of Wild/Hatchery Steelhead Interactions Within A Large, Complex Watershed Research Partners: WDFW Skagit River System.
Contribution of Resident O. mykiss to Anadromous Populations and Vice Versa: Implications for Recovery Strategies and VSP Analysis Richard W. Carmichael.
Washington’s Lower Snake River Compensation Plan Steelhead Program – A retrospective and program adaptive management overview Mark Schuck and Joe Bumgarner.
Migration pathway, age at ocean entry, and SARs for Snake River Basin fall Chinook prior to summer spill at LGR, LGS, and LMN dams.
Is there evidence for stock segregation in Chinook salmon during ocean residence? Indicators of survival: reconstruction of juvenile size-at-emigration.
Effectiveness of alternative broodstock, rearing and release practices at Winthrop NFH William Gale and Matt Cooper -USFWS, Mid-Columbia River Fishery.
DEVELOPING A NOMENCLATURE FOR STEELHEAD, COHO, CUTTHROAT AND OTHER ANADROMOUS SALMONIDS WITH EXTENDED FRESHWATER REARING Hal Michael, John McMillan, Bob.
Chinook Salmon Supplementation in the Imnaha River Basin- A Comparative Look at Changes in Abundance and Productivity Chinook Salmon Supplementation in.
Why is there a difference in sex ratio between hatchery and wild steelhead? Neil Thompson1, Kassi Cole2, Laura McMahon1, Melanie Marine1, Lyle Curtis.
 Present in Snake, Clearwater, and Salmon River drainages  Provide valuable fishery  Well documented variation in ocean life history (A vs B run) 
Overview of the Alligator Gar Conservation Management Plan for Alabama Dave Armstrong Alabama Division of Wildlife & Freshwater Fisheries Spanish Fort,
Variation in the effectiveness of alternative broodstock, rearing, and release practices among three supplemented steelhead populations - Hood Canal, WA.
Comparison of Winter Steelhead Trap Estimates in Small Basins to Other Escapement Methods and the Representativeness of ODFW Life-Cycle Monitoring Sites.
Supplementation using steelhead fry: performance, interactions with natural steelhead, & effect of enriched hatchery environments Christopher P. Tatara.
Objective Determine how using 9mm tags may affect our current research project in the John Day Basin.
1 Independent Scientific Advisory Board June 12, 2003 A Review of Salmon and Steelhead Supplementation.
2010 work planned, new operations, and wrap up Presenter: Robin Ehlke CSS Annual Meeting Apr 2 nd 2010.
Survival and Behavior of Juvenile Chinook Salmon in the Lower Columbia River, Estuary, and Plume G. A. McMichael 1, R. L. McComas 2, J. A. Carter 1, G.
Joe Bumgarner Washington Department of Fish and Wildlife.
Estuary Actions for Salmon and Steelhead Columbia River Estuary Science Policy Exchange September 10-11, 2009 NOAA 2008 FCRPS Biological Opinion Estuary.
Ocean rivers SARs LGR-LGR SARs LGR-LGR Harvest Mouth of Columbia predicted returns Mouth of Columbia predicted returns Juvenile travel time and survival.
Hood Canal Steelhead Acoustic Telemetry Studies Barry Berejikian and Skip Tezak NOAA Fisheries Northwest Fisheries Science Center Manchester Research Station.
Performance of a New Steelhead Line Derived from Hatchery Parents Collected in Autumn in the Grande Ronde River Lance Clarke, Michael Flesher, Shelby Warren,
Implementing Hatchery Reform The Dawn of a New Beginning or more of the same old thing? Mike Delarm NOAA Fisheries.
California Department of Fish and Game Klamath-Trinity Project Klamath Basin Chinook Salmon Spawning Escapement, Harvest and Age Composition Fish and Game.
Estimated survival of juvenile salmonids through the lower Columbia River and estuary, and estimated mortality from avian predation John Ferguson NOAA.
Payette MPG Sockeye Adult Tributary Juvenile Data Tributary Data
Age at ocean entry of Snake River Basin fall Chinook and its significance to adult returns prior to summer spill at LGR, LGS, and LMN dams.
MPG Spring-Summer Chinook
Snake River MPG Fall Chinook Adult Tributary Juvenile Data Tributary
2017 TMT Year-end Review December 12, 2017 Brandon R. Chockley
Hatchery Production Wells Hatchery Steelhead: 450,000 fish annually
Eagle Fish Genetics Lab (IDFG): Craig Steele Mike Ackerman
Presentation transcript:

Alsea Steelhead Acoustic Tagging Project

ODFW -Salmonid Life Cycle Monitoring Project Alsea Steelhead Acoustic Tagging Project EPA – Estuarine Habitat Project (HMSC) ODFW –Mid-coast Management District Collaborators:

Alsea Steelhead Acoustic Tagging Project Determine “Survival” and Migration Timing for Three Steelhead Smolt Release Groups : Determine “Survival” and Migration Timing for Three Steelhead Smolt Release Groups : 1. Traditional Hatchery Brood 2. New Hatchery Brood 3. Naturally Reared Specifically Compare: Specifically Compare: “Survival” through River “Survival” through River “Survival” through Estuary “Survival” through Estuary Migration Timing Migration Timing Estuary Rearing Estuary Rearing

Acoustic Receiver Transmitter Steelhead Smolt 75 transmitters / group

Head of Tide N. Fk. Hatchery Crooked Creek Campbell Park Fall Creek Alsea Steelhead Acoustic Tagging Project Acoustic Receiver Locations Fiver Rivers Estuary 5 River Sites – 11 Receivers 7 Estuary Sites – 15 Receivers 1 Ocean Sites – 5 Receivers

Alsea Head of Tide Acoustic Receiver Array Receiver # 1 Receiver # 2 Receiver # 3

Receiver # 1 Receiver # 2 Acoustic Receiver Array Mid-Estuary

Alsea Jaws Receiver # 2 Receiver # 1 Receiver # 4 Receiver # 3

Alsea Steelhead Acoustic Tagging Project Determine Survival and Migration Timing for Three Steelhead Smolt Release Groups : Determine Survival and Migration Timing for Three Steelhead Smolt Release Groups : 1. Traditional Hatchery Brood 2. New Hatchery Brood 3. Naturally Reared Specifically Compare: Specifically Compare: Survival Through River Survival Through River Survival through Estuary Survival through Estuary Migration Timing Migration Timing Estuary Rearing Estuary Rearing

Hatchery Reared Smolt Naturally Reared Smolt Age 1+ Mostly Age 2+ Avg. Wt ~35 gms Avg. Wt ~75 gms

Length Frequency - Steelhead Smolts Traditional Hatchery Broodstock

New Hatchery Broodstock Length Frequency - Steelhead Smolts ~ 15 % of Population < 160 mm

Length Frequency Naturally Reared Steelhead Smolts

3.3 gms 1.6 gms V9 TagV7 Tag All Naturally Reared Smolts All Hatchery Reared Smolts <170 mm Tagging Criteria: Tag weight < 5% of Fish body weight V7 Tags 24 Hatchery Reared Smolts mm

Tagging Dates: Traditional Broodstock March New Broodstock March Release Dates: Traditional Broodstock April 2-9 New Broodstock April 2-9 Hatchery Smolts Sample Size: Traditional Broodstock 74 Fish New Broodstock 76 Fish

Crooked Creek Tagging Naturally Reared Smolts

Tagging Dates: March 17 – April 18 Release Dates: March 18 – April 19 Naturally Reared Smolts Recovery Period: 24 hours Sample Size: 72 Fish

V7 vs V9 Transmitters Results Detection Rate at Receiver Arrays Migration Rate by Release Group Survival Rate by Release Group Estuary Residence by Release Group

Receiver Array Detection Rate V7 versus V9 Transmitters

V7 vs V9 Transmitters Results Detection Rate at Receiver Arrays Migration Rate by Release Group “Survival Rate” by Release Group Estuary Residence by Release Group

“Survival” Rate by Release Group “Survival” Rate in River (to Head of Tide) Traditional Broodstock 80% New Broodstock 71% Naturally Reared 74% Fall CreekHead of Tide

“Survival” Rate by Release Group Survival Rate in Estuary (Head of Tide to Jaws) Traditional Broodstock 44% New Broodstock 59% Naturally Reared 53% Fall CreekHead of Tide

“Survival” Rate by Release Group Survival Rate to Ocean Traditional Broodstock 35% New Broodstock 42% Naturally Reared 39% Head of TideFall Creek

Number Released In-River Mortality Estuary Mortality Smolts to Ocean Traditional B. Stock 60,00012,00026,88021,000 New B. Stock 60,00017,40017,46625,200 Total120,00029,40044,34646,200 Hypothetical Release and Resulting Mortality

Number Released In-River Mortality Estuary Mortality Smolts to Ocean Ocean Mortality Adult Return Trad. B. Stock 60,00012,00026,88021,000 New B. Stock 60,00017,40017,46625,200 Total120,00029,40044,34646,200 Hypothetical Release and Resulting Mortality ~41, ,200 38,200 ~5,000 – 8,000 8,000

Number Released In-River Mortality Estuary Mortality Smolts to Ocean Ocean Mortality Adult Return Trad. B. Stock 60,00012,00026,88021,000 New B. Stock 60,00017,40017,46625,200 Total120,00029,40044,34646,200 Hypothetical Release and Resulting Mortality ~41, ,200 38,200 ~5,000 – 8,000 8,000 (26 %) (39 %) (35 %)

V7 vs V9 Transmitters Results Detection Rate at Receiver Arrays Migration Rate by Release Group “Survival” Rate by Release Group Estuary Residence by Release Group

Migration Rate by Release Group Fall CreekHead of Tide Mean Min. Max Traditional Broodstock New Broodstock Naturally Reared

River Migration Rate vs Size of Smolts New Hatchery Broodstock

Naturally Reared Smolts River Migration Rate vs Size of Smolts

V7 vs V9 Transmitters Results Detection Rate at Receiver Arrays Migration Rate by Release Group “Survival” Rate by Release Group Estuary Residence by Release Group

Estuary Residence Survivors vs Non-Survivors 198mm 199mm 195mm 197mm 170mm 172mm

Estuary Residence vs Size of Fish New Hatchery Broodstock

Estuary Residence vs Size of Fish Naturally Reared Smolts

ConclusionsSurvival: All 3 groups showed significant mortality prior to entering ocean (58-65%) For Hatchery Releases, In River/Estuary mortality higher than Ocean mortality: In River Mortality: 26% Estuary Mortality: 39% Ocean Mortality: 34%

ConclusionsSurvival: Traditional vs New Broodstock: In-River “Survival”: Trad. B. Stock: Highest New Broodstock Lowest (small, non- migrants?) Estuary Survival: Trad. B. Stock: Lowest New B. Stock: Highest

Conclusions Survival: Survival: Trad. B.Stock vs New B.Stock vs Nat. Reared: In-River “Survival”: Trad. B. Stock: Highest Nat. Reared New Broodstock Lowest (small, non- migrants?) Estuary Survival: Trad. B. Stock: Lowest Nat. Reared New B. Stock: Highest

Conclusions Migration Timing and Estuary Residence Migration Timing and Estuary Residence Average migration time through the river was days for all three release groups. Average migration time through the estuary was 2-8 days for successful migrants. Average migration time through the estuary was 2-8 days for successful migrants. Hatchery reared smolts stayed in estuary longer than naturally reared smolts. Hatchery reared smolts stayed in estuary longer than naturally reared smolts. Fish that remained in estuary longer suffered higher mortality. Fish that remained in estuary longer suffered higher mortality. Estuary residence time was not related to fish size. Estuary residence time was not related to fish size.

Acknowledgments Polly Rankin and ODFW Marine Program Funding: Restoration and Enhancement Program Oregon Hatchery Research Center

DownstreamUpstream ? %

Alsea Winter Steelhead Harvest & Corresponding Smolt Release