One more step towards operational management of the world...

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Patrick Lehodey Marine Ecosystems Modeling and Monitoring by Satellites CLS, Space Oceanography Division 8-10 rue Hermes, 31520 Ramonville, France [email protected] One more step towards operational management of the world largest tuna fishery

Transcript of One more step towards operational management of the world...

  • Patrick Lehodey

    Marine Ecosystems Modeling and Monitoring by Satellites

    CLS, Space Oceanography Division

    8-10 rue Hermes, 31520 Ramonville, France

    [email protected]

    One more step towards

    operational management of the

    world largest tuna fishery

    mailto:[email protected]

  • SEAPODYM

    Ocean biogeoch.

    3-D Models

    Satellite data

    Primary Prod.

    From physics to fish (er)

    Ocean Physics

    3-D models

    Satellite data

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    60- 20- 100102030405060708090100110120130140150160170180- 170- 160- 150- 140- 130- 120- 110- 100- 90- 80- 70- 60- 50- 40- 30- 20

    - 20- 100102030405060708090100110120130140150160170180- 170- 160- 150- 140- 130- 120- 110- 100- 90- 80- 70- 60- 50- 40- 30- 20- 60

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    Total prises 90-97 8000YFTSKJ

    BFT

    ALB

    BET

    Blue = skipjack; yellow = yellowfin; Red = bigeye

    FISHERIES

    (kindly from A. Fonteneau)

    Fish population

    dynamic models

    predator

    Ocean Mid-

    Trophic Levels

    prey

    ?

  • 3

    stomach content

    of a yellowfin tuna

    Credit: Frédéric MENARD, IRD, France

    First step: modeling MTL

    Time of development in days (Log scale)

    of mid-trophic organisms in relation to

    their ambiant habitat temperature Tc

    Lehodey P., Murtugudde R., Senina I. (2010). Bridging

    the gap from ocean models to population dynamics of

    large marine predators: a model of mid-trophic

    functional groups. Progress in Oceanography, 84: 69–84

  • day

    night

    sunset, sunrise

    Epipelagic layer

    T, U, V

    surface 1 2 3 4 5 6

    Mesopelagic layer

    T, U, V

    Bathypelagic

    Layer

    T, U, V

    Day length

    = f(Lat, date) PP

    E

    En’

    Mar-ECO station North Atlantic, (IMR, Bergen Norway) showing acoustic detection of micronekton

    Micronekton conceptual Model

    0 m

    500 m

    A model of micronekton

    (small prey organisms)

    The MODEL: 6 functional groups in 3 vertical

    layers. Three components exhibit diel vertical

    migrations, transferring energy from surface to

    deep layers.

    The source of energy is the primary production

    PP.

  • Epipelagic (daytime)

    micronekton (2005)

    Production (g m-2 d-1)

    Biomass (g m-2)

    Results: P/B epipelagic micronekton

    ¼ deg x 6 day

    Physical fields from

    MERCATOR

    (http://www.mercator-ocean.fr/)

    Satellite derived Primary

    production

    http://www.mercator-ocean.fr/http://www.mercator-ocean.fr/http://www.mercator-ocean.fr/

  • day

    night

    sunset, sunrise

    Epipelagic layer

    surface1 2 3 4 5 6

    Mesopelagic layer

    Bathypelagic layer

    day

    night

    sunset, sunrise

    Epipelagic layer

    surface1 2 3 4 5 6

    Mesopelagic layer

    Bathypelagic layer

    References:

    Lehodey et al. (1998). Fish. Oceanog.

    Lehodey, (2001). Prog. Oceanog.

    Lehodey et al. (2010 ) Prog. Oceanog.

    Results: day/night epipelagic biomass

    1/12th deg x 6 day

    Physical fields from MERCATOR

    (http://www.mercator-ocean.fr/)

    Satellite derived Primary

    production

    http://www.mercator-ocean.fr/http://www.mercator-ocean.fr/http://www.mercator-ocean.fr/

  • Assimilation of acoustic data in the MTL model:

    The ratios Predicted biomass / Observed signal (NASC) between layers and between day and

    night are used to optimize the coefficient matrix of Energy transfer between functional groups.

    Data assimilation

  • Page 8

    Optimization: Hawaiian transect

  • Page 9

    Validation: Tasmanian transect

    Data provided by R. Kloser (CSIRO)

  • Age-structured

    Population Growth

    mortality

    by

    cohort

    Feeding Habitat = Food (MTL) abundance

    x accessibility (T,DO)

    Spawning Habitat = Food & T for larvae

    Absence of larvae

    predators (MTL)

    IF MATURE

    Seasonal

    switch

    Movement toward

    feeding grounds

    Movement toward

    spawning grounds

    Mortality

    Spawning success

    Recruitment

    (larval drift)

    Page

    10

    Fisheries

    Predicted

    catch

    Observed

    effort/catch

    Calibration

    The prediction of MTL is the key to understand and model The population dynamics of their predators, e.g., tunas

    Application to exploited species

  • Parameter estimation approach

    K

    a rji

    jiajifaf

    rji

    jiajifaf

    predraft

    K

    a

    jiaaafjiftfpred

    jift

    yxNE

    yxNEs

    Q

    yxNwsEqC

    1 ,

    ,,,,,

    ,

    ,,,,,

    ,,,

    1

    ,,,,,,,,, ,

    2sin1

    2

    1

    ))1(ln(ln

    ln

    2

    ,,,,,,

    ,,,2

    ,,,

    ,

    kkkkk

    prraft

    obsraft

    raft f

    LF

    t f t f

    obsft

    predft

    obsft

    t f

    predft

    obs

    QQL

    CCC

    CCL θ

    Model predictions

    Likelihoods, parametric space

  • The world’s largest tuna fishery catch ~2 Million t/yr of skipjack

    in the western central Pacific Ocean. This is the main

    economical resource of Pacific Island Countries, that want to

    manage it in a sustainable way and to obtain a MSC label.

    Background:

    Application to the largest tuna fishery

    To conserve this label, PICs needs to demonstrate they have appropriate (spatial)

    tools to manage the stock, accounting for the fishing effort outside of their EEZs.

    Total predicted skipjack biomass (2009)

    And observed catch rates (circles)

    -> Detailed spatial population dynamics (larvae to oldest adults) and catch

  • 0.25°

    SODA, February 2002 , 1° GLORYS, February 2002 , 0.25° NCEP, February 2002, 2°

    OPA-NCEP (http://www.nemo-ocean.eu/; http://www.cgd.ucar.edu/cas/guide/Data/ncep-ncar_reanalysis.html)

    SODA (http://www.atmos.umd.edu/~ocean/)

    GLORYS (http://www.mercator-ocean.fr/)

    Interest for operational approach

    Before the real time monitoring, there is a strong interest for

    improving the stock estimates and their fluctuations under

    both Climate (natural and anthropic) and Fishing impacts

    A realistic mesoscale provides a better signal for parameter estimation

    Spatial and temporal fit is improved

    http://www.nemo-ocean.eu/http://www.nemo-ocean.eu/http://www.nemo-ocean.eu/http://www.cgd.ucar.edu/cas/guide/Data/ncep-ncar_reanalysis.htmlhttp://www.cgd.ucar.edu/cas/guide/Data/ncep-ncar_reanalysis.htmlhttp://www.cgd.ucar.edu/cas/guide/Data/ncep-ncar_reanalysis.htmlhttp://www.atmos.umd.edu/~ocean/http://www.mercator-ocean.fr/http://www.mercator-ocean.fr/http://www.mercator-ocean.fr/

  • ESSIC ORCA2-PISCES SODA-PPsat

    GLORYS-PPsat

    30d x 2

    30d x 1

    7d x 0.25

    Note: Parameterization obtained with SODA is simply scaled for GLORYS

    Stock estimation is

    improved (less diffusion)

    ORCA2-PISCES

    Interest for operational approach

  • Goodness-of-fit for catch and CPUE (1975-2003)

    Validation (Skipjack)

    Indian Ocean experiment

    1997, II quarter

    1997, IV quarter

    Predicted vs. observed catch & LF

    Sub-tropical pole-and-line (solid lines – predicted catch)

    Tropical purse-seine (free schools)

  • 7th regular session of

    the Scientific Committee

    Pohnpei, Micronesia,

    8-17 August 2011

    Observed catch rates (black dots) and monthly

    predictions of skipjack total biomass (2009)

    EEZ of Papua New Guinea

    (weekly)

    (weekly)

    Towards real time monitoring?

  • Page 17

    By providing realistic reanalyses of ocean physics, OO allows a better

    parameter estimation of biological models (by increasing spatio-temporal fit

    between data and prediction).

    OM applications are being developed. The coming next step is the

    validation and use of real time applications for the monitoring of fisheries.

    Operational biogeochemical models are complementary to PPsat with

    several advantages:

    - Fully coherent with physics (resolution, no gaps, meso and submeso…)

    - Include other key variables (DO, pH?, pollutants…)

    - Provide hindcasts that are absolutely critical for estimating and

    validating fish stock evolution over historical periods (50 yrs typically),

    and limiting the impact of initial conditions in the optimization approach.

    - Provide forecasts (week, season, internannual, decadal, IPCC)

    - Allow testing scenarios for impact studies, e.g., tracers Cs, Hg…

    - PPsat is also an (empirical) model with many sources of uncertainties.

    Conclusions