scientific talk on responses of fish populations to climate forcing across the north atlantic

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Presented by: Geir Ottersen, Institute of Marine Research, Bergen, Norway Coauthors: Nils Chr. Stenseth, Kyrre Lekve, and Dag Hjermann University of Oslo, Norway Responses of fish populations to climate forcing across the North Atlantic Comparative studies of North Atlantic ecosystems 2 nd GLOBEC Open Science Meeting Comparative Ecosystems and Climate Change 15-18 October 2002, Qingdao, P. R. China

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  • Presented by: Geir Ottersen, Institute of Marine Research, Bergen, Norway

    Coauthors: Nils Chr. Stenseth, Kyrre Lekve, and Dag Hjermann University of Oslo, Norway

    Responses of fish populations to climate forcing across the North Atlantic

    Comparative studies of North Atlantic ecosystems

    2nd GLOBEC Open Science Meeting Comparative Ecosystems and Climate Change

    15-18 October 2002, Qingdao, P. R. China

  • 2nd GLOBEC Open Science Meeting Comparative Ecosystems and Climate Change

    15-18 October 2002, Qingdao, P. R. China

    FOCUS

    Through examples from the North Atlantic I will show that the response of a fish population to a climate signal may be

    To explain these response patterns we must also understand the mechanisms involved. Examples of how Enrichment, Concentration, and Retention processes may affect North Atlantic fish populations will be given.

    Unlagged/lagged Linear/nonlinear

    Direct/indirect

    In interaction with other (non-climatic) factors

  • Russia

    Barents Sea Greenland

    80W 40 0 40 80E

    80N

    60

    40

    The North Atlantic

    North Sea

    Newfoundland

    Georges Bank

  • A B A

    Climate Climate

    Direct response

    Indirect response

    Ecological response to climate fluctuations I

  • Through physiology, (metabolic and reproductive processes)

    Direct response to climate

    Through biotic environment (predators, prey, species interactions, and disease)

    and abiotic environment (habitat type and structure).

    Indirect response to climate

  • 4 YEARS OLD COD

    3,0 3,2 3,4 3,6 3,8 4,0 4,2 4,4 4,6 4,8 5,0

    -1,5 -1 -0,5 0 0,5 1 1,5

    Temperature anomaly (C)

    Mea

    n w

    eigt

    h (k

    g)

    R2=0.67

    Brander and OBrien (2000)

    Departure from mean weight at age 4

    1960 1970 1980 1990 2000 Year Class

    0

    -1

    +1

    Temperature anomaly (C)

    Departure from mean weight at age 3

    The effect of temperature on weight of North Sea cod

    Direct response to climate

  • Time

    Match Peak first feeding of cod larvae

    Peak production copepod nauplii

    Mismatch Peak first feeding of cod larvae

    Peak production copepod nauplii

    Time

    The match-mismatch hypothesis

    Col

    d

    War

    m

    Indirect response to climate

    Hjort (1914); Cushing (1982)

  • At At-i

    Climatet Climatet-i

    Unlagged response

    Lagged response

    At

    Ecological response to climate fluctuations II

  • NAO and Barents Sea cod abundance Lo

    g(ab

    unda

    nce

    age

    3)

    NAO index spawning year NAO index spawning year

    Temperature

    Tem

    pera

    ture

    Temperature

    Log(

    abun

    danc

    e ag

    e 3)

    Length yr old cod (mm)

    Leng

    th

    yr o

    ld c

    od (m

    m)

    Ottersen and Stenseth (2001)

    Temporal delay in ecological response to climate fluctuations

  • Linear climate signal causes shift in ecological state when climate threshold passed.

    Linear ecological response to climate signal

    Clim

    ate

    Time

    Ecol

    ogic

    al

    Res

    pons

    e

    Single climate event causes shift in ecological state

    A B C

  • Drinkwater (2002)

    A Linear ecological response to climate signal

    Growth of Canadian Northern Cod B

    ody

    mas

    s cha

    nge

    (g)

  • Climate induced crash in Peruvian anchovy stock

    Human and

    Single climate event causes shift in ecological state B

    El Nio:

  • Physical processes of importance to marine ecology

    Enrichment processes makes more nutrients available to biological productivity

    Concentration processes enhances food availability for a predator by increasing the concentration of food particles

    Bakun (1996)

    Retention processes work towards keeping individual members of a population in the appropriate place during the various parts of the life cycle

  • Concentration processes:

    General example: Encounter-rate increases/decreases as a result of variability in micro-scale turbulence

    Rothschild and Osborn (1988)

    More specific case: Cod larval feeding success related to turbulence induced contact rate with main prey Calanus finmarchicus nauplii

    Sundby and Fossum (1990); Sundby et al.(1994)

  • Retention processes: Example: Stability of current patterns to which life cycles are adapted Hypothesis: Member-vagrant Sinclair and Iles (1989) Physical features: Wind direction, residual currents, advection Biological feature: Survival through enhanced feeding success and reduced predation risk

    Georges Bank case Serchuk et al. (1994); Werner et al. (1993)

  • Cod and Haddock spawn on the NE corner of Georges Bank and are slowly transported

    around the bank as the larvae mature

    Dr B. Monger, Cornell University (pers. com.)

  • Typical recirculation current pattern that retains cod and haddock larvae around Georges Bank

    B. Monger

  • Break in the typical recirculation current pattern, caused by wind events or impinging Gulf Stream Rings, leading

    to Advective Loss of cod and haddock larvae

    B. Monger

  • A

    B A

    Climate Climate

    Interactions with other factors

    B

    Ecological response to climate fluctuations III

  • Sundby (2000)

    Distribution of Atlantic cod and sea temperatures at 100m depth

    Atlantic cod

    Greenland

    UK

    Spain

  • Effects of temperature fluctuations on recruitment to Atlantic cod stocks:

    Recruitment to cold-water stocks increases with increasing temperature

    Recruitment to warm-water stocks decreases with increasing temperature

    Recruitment to stocks in intermediate temperatures shows no clear response to temperature variability.

    Ottersen (1996); Planque and Fredou (1999)

    A possible mechanism (Sundby 2000): Temperature variability is linked to advection of the cods main food items, Calanus finmarchicus from core production regions.

  • Norway

    Distribution of Calanus finmarchicus

    Atlantic water Arctic water Coastal water

    Water masses Sundby (2000)

    UK

    Greenland

    Spain

  • Higher temperatures

    Lower temperatures

    Schematic view of the North Atlantic

    Isotherms

    Sundby (2000)

  • Flow of water masses and Calanus to stocks of lower ambient temperature

    Flow of water masses and Calanus to stocks of similar ambient temperature

    Temperature-cod link as a proxy for Calanus-cod link

    Flow of water masses and Calanus to stocks of higher ambient temperature

    Sundby (2000)

  • 2nd GLOBEC Open Science Meeting Comparative Ecosystems and Climate Change

    15-18 October 2002, Qingdao, P. R. China

    CONCLUSIONS

    Through examples from the North Atlantic I have shown that the response of a fish population to a climate signal may be

    To explain these response patterns we must also understand the mechanisms involved. Examples of how Enrichment, Concentration, and Retention processes may affect North Atlantic fish populations have been given.

    Unlagged/lagged in time Linear/nonlinear

    Direct/indirect

    In interaction with other (non-climatic) factors

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