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Life-cycle models for the diverse and plastic Oncorhynchus mykiss: challenges and opportunities Neala Kendall , Rich Zabel § , and Tom Cooney § * Washington Department of Fish and Wildlife § NOAA Fisheries, Northwest Fisheries Science

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  • Life-cycle models for the diverse and plastic Oncorhynchus mykiss:

    challenges and opportunities

    Neala Kendall*§, Rich Zabel§, and Tom Cooney§

    *Washington Department of Fish and Wildlife §NOAA Fisheries, Northwest Fisheries Science

  • Oncorhynchus mykiss life history tactics and population dynamics

    • Life history strategies influenced by environmental and

    anthropogenic factors

    • Life-cycle models used to better understand strategies,

    evaluate population dynamics spatially and temporally

    Jonny Armstrong John McMillan

  • Purpose of a life-cycle model

    • Questions to answer using the model:

    – Is anadromy expected to persist into the future?

    – Under what environmental conditions will O. mykiss

    be resident or anadromous?

    – What life history stages represent population

    “bottlenecks?”

    – What patterns of anadromy and residency will we see

    given different freshwater habitat mitigation actions?

  • Decision to smolt

    O. mykiss life cycle models

    Freshwater Ocean

    Growth

    Maturation

    Decision to return & spawn

    Natural mortality

    Migration to ocean as steelhead

    trout

    Mature fish

    Maturing fish

    Mature fish

    Modified from Theriault et al. 2008

    Growth

    Maturation

    Spawning

    Natural mortality

    Maturing fish

    Mature fish

    Mature fish

    Immature fish

    Immature fish

    Spawning migration

    Fishing and

    natural mortality

    Ocean migration

    Mortality

    Natural mortality

    Immature fish

    Mature fish

  • Existing models to help

    1. Yakima River, WA anadromous/resident O. mykiss abundance and reproductive success life-cycle models (I. Courter & C. Frederiksen et al.)

    2. Anadromy/residency and smolt age decision for O. mykiss (originally developed for CA populations; Satterthwaite et al. 2009, 2010)

    3. Chinook and O. mykiss life-cycle matrix models for Interior Columbia River basin (but only anadromous component; ICTRT and Zabel 2007)

  • Yakima River O. mykiss life-cycle models

    Cross-Ecotype

    Exchange

    Capacity

    Fecundity

    Flow

    Habitat Area

    (PHABSIM & 2D modeling)

    Anadromous

    Spawners

    Resident

    Spawners

    Freshwater SurvivalMarine Survival

    Body Size

    Growth

    (bioenergetics)

    Temperature

    Food Supply

    Territory Size

    (competition)

    Abundance

    Fry

    Environmental

    Conditions

    Reproductive

    Success

    Survival

    Courter et al. 2009

    • Use freshwater food

    supply, flow, and

    temperature to predict

    fish growth, survival,

    capacity, and reproductive

    success by life history

    tactic

  • Model predictions

    Anadromous Resident

    Courter et al. 2009

  • Anadromy/residency life-cycle model for O. mykiss

    • Based on fish emergence date, freshwater growth,

    survival, fecundity, and overall fitness

    • Predict maturation/residency and smolt age decision

    Satterthwaite et al. 2009, 2010

    Maturation decision smolting decision

  • Model predictions

    • Predict maturation/

    residency and smolt

    age decision

    Satterthwaite et al. 2009, 2010

    Gro

    wth

    rate

    (m

    m/d

    ay)

    Emergence date

    Maturity of age-0 females

    mature

    wait, smolt at age 0

    mature

    wait, smolt at age 1

  • O. mykiss matrix models for Interior Columbia River basin

    • Steelhead-only life-cycle model

    • Beverton-Holt functions to include density-dependent survival in freshwater

    • Components (adjusted in different “scenarios”):

    – Downstream survival (based on hydropower corridor passage)

    – Estuary and early marine survival (based on climate conditions)

    – Later marine survival

    – Harvest, upstream survival

    – Overwinter survival in fw

    ICTRT and Zabel 2007, Zabel et al. 2013

  • Interior Columbia River basin populations

    • Rapid River (Little Salmon River)

    • Potlatch River

    • Catherine Creek

    • Umatilla River

    • Toppenish Creek

    • Naches River

    • Satus Creek

    • Upper Yakima River

    Photo: John McMillan

  • Example model run—Umatilla River

    20 40 60 80 100

    0

    1000

    2000

    3000

    4000

    5000

    6000

    sp

    aw

    ne

    rs.r

    aw

    [, , 3

    ]P

    op

    ula

    tio

    n a

    bu

    nd

    ance

    Years into the future

    50 fish

  • • Abundance decreased over time for Yakima River

    basin and Umatilla River populations

    • Abundance increased over time for Potlatch

    River, Catherine Creek, & Rapid River populations

    Model predictions (under baseline scenarios)

  • • Changes in habitat, upriver survival, and estuary/early ocean conditions resulted in largest spawner abundance changes

    • Changes in habitat resulted in greatest changes in quasi-extinction probability

    • Changes in harvest rates resulted in smaller abundance and extinction probability changes

    Model predictions (under varying scenarios)

  • Population-specific model predictions under various scenarios—Umatilla River

    Survival through the hydropower corridor

    Po

    pu

    lati

    on

    ab

    un

    dan

    ce

    afte

    r 1

    00

    ye

    ars

    Estuary and early marine survival

    Survival through the hydropower corridor

    Habitat (overwinter/ prespawning survival)

  • Population-specific model predictions under various scenarios—Umatilla River

    Later marine survival

    Estuary and early marine survival

    Estuary and early marine survival

    Harvest rate

    Po

    pu

    lati

    on

    ab

    un

    dan

    ce

    afte

    r 1

    00

    ye

    ars

  • Future work

    • Combine ICTRT and Zabel matrix model with Courter & Frederiksen et al. freshwater habitat conditions determinants and Satterthwaite et al. model of anadromy/residency decision

    Photos: John McMillan

  • Habitat considerations need to be incorporated

    • First establish fish-specific side of the life-cycle model

    • Then incorporate freshwater habitat considerations into model

    • Understand how habitat changes (climate change and human modifications including restoration) may affect abundance and viability

  • Incorporating habitat restoration into the models

    • Develop landscape-to-habitat functional relationships

    • Develop habitat-to-fish relationships

    • Model habitat quality (e.g., flow and temperature) and quantity using land-use and geomorphic characteristics to estimate fish capacity and survival

    Bartz et al. 2006, Scheuerell et al. 2006, Beechie et al. 2006

  • Acknowledgements • National Research Council Postdoctoral Fellowship Program

    • Interior Columbia TRT life-cycle modeling group

    • Ian Courter (Mt. Hood Consulting), Chris Frederiksen (Yakama Nation), Ethan Crawford (WDFW), ODFW La Grande office, Brett Bowersox (IDFG), and others who supplied data

    Photo: John McMillan

    • NOAA Northwest Fisheries Science Center

    • WDFW, especially Erik Neatherlin, Jeremy Cram, Andrew Murdoch, and Thomas Buehrens

  • Questions?

  • Oncorhynchus mykiss: one (two?) cool fish

    Photo: John McMillan

  • Oncorhynchus mykiss: one (two?) cool fish

    • Very diverse life history including migration tactics (“partial migration”)

    • Valuable recreational and commercial fisheries

    • Many natural populations have declined in abundance and

    life history diversity over the past century, are ESA listed

    Photos: Jonny Armstrong

  • Population-specific model predictions under various scenarios—Umatilla River

    Habitat (overwinter/prespawning survival)

    Po

    pu

    lati

    on

    ab

    un

    dan

    ce

    Estuary and early marine survival

    Later marine survival