One more step towards operational management of the world...
Transcript of 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
One more step towards
operational management of the
world largest tuna fishery
mailto:[email protected]
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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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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
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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
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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.
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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/
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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/
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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
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Optimization: Hawaiian transect
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Validation: Tasmanian transect
Data provided by R. Kloser (CSIRO)
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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)
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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
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Parameter estimation approach
K
a rji
jiajifaf
rji
jiajifaf
predraft
K
a
jiaaafjiftfpred
jift
yxNE
yxNEs
Q
yxNwsEqC
1 ,
,,,,,
,
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2sin1
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ln
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,,,
,
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
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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
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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/
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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
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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)
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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?
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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