Predicting skipjack tuna dynamics and effects of climate change using SEAPODYM with fishing and tagging data

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Predicting skipjack tuna dynamics and effects of climate change using SEAPODYM with fishing and tagging data Working Doc.: WCPFC-SC12-2016/EB WP01 Inna Senina 1 Patrick Lehodey 1 Beatriz Calmettes 1 Simon Nicol 2 Sylvain Caillot 3 John Hampton 3 and Peter Williams 3 1 CLS, Marine Ecosystems Department, Ramonville St Agne France 2 Department of Agriculture and Water Resources, Canberra, Australia 3 SPC, Oceanic Fisheries Programme, Noumea, New Caledonia

Outlines - SEAPODYM 3.0 - Pacific Skipjack optimization experiments - Stock estimates - Climate change projections - Perspectives

SEAPODYM 3.0 Fully explicit spatial representation of fish population dynamics Include Fish movements (currents + swimming) Population, not only «stock», meaning it includes spawning and larval stages Based on mechanisms that control life stage dynamics and relying on physical and biological characteristics of the ecosystem Using all detailed spatially disaggregated data in parameter optimization (i.e., Max. Likelihood Estimation as in Multifan-CL) Search for overall species parameterization, ie valid everywhere at basinscale or even globally Allowing to predict fish distribution even where there is no catch information Less dependent from fishing data (especially effort) than standard S/R models Becomes dependent of environmental data accuracy

SEAPODYM 3.0 In each cell of the grid domain, at each time step, the model computes: the production and biomass of ecosystem functional groups (zooplankon and micronekton) that are prey of large fish the density of fish for each age-cohort from larvae recruits to oldest adult Size (cm) of fish Predicted skipjack density (all cohorts aggregated) and observed catch rates (% to circles) the predicted catch by age (size) if a (observed or simulated) fishing effort for a defined fishery is available (or simulated). Resolution: 1/4 x week

SEAPODYM 3.0 Major changes in new version (3.0): 1. Revision of the spawning habitat with prey and predator functions defined separately (instead of using the prey-predator ratio as in previous version). 2. one additional parameter associated to each functional group of prey can be estimated providing more flexibility in the representation of vertical behavior and access to tuna forage. 3. Implementation of alternative approach to account for fishing mortality and to predict catch without fishing effort, i.e. based on observed catch and model biomass only, which can be particularly useful when reliable fishing effort is not available. 4. Use of Tagging data in the Maximum Likelihood Approach for parameter estimation (pre-processing with geo-statistical methods before integrating observed tag recapture data).

Pacific Skipjack optimization

Pacific Skipjack optimization Mean monthly distributions of skj larvae (2001-2010) with E3 Estimated parameters in the optimization experiments

Pacific Skipjack optimization Estimated parameters in the optimization parameters Observed tag recaptures (a) and predicted using parameter estimates of E1 (b).and E2 (c). Red circles are releases.

Skipjack stock estimates Mean distribution 1980-2010 Immature skj: age 3 to 9 months Adult skj: > 9 months Catch prediction method LL E1 PL effort PS- catch removal Catch, LF E2 Catch removal Catch, LF, tags E3 PL effort PS- catch removal Catch, LF, tags

Regional comparison between SEAPODYM (black line: dashed E2; solid E3) and MULTIFAN-CL estimates for total skipjack biomass Skipjack stock estimates

Skipjack stock estimates Fishing impact Figure 3: Pacific-wide total skipjack stock estimate with and without fishing (E2 = thin line; E3 = thick lines) End 2010: 20% (total) 25% (Spawning B) Spatial fishing impact on young immature and adult skipjack for E3 experiment. Contour lines show the index [ B F0 - B ref ] / B F0 and colour shows the average biomass reduction due to fishing

Climate change projections Projection without fishing IPCC scenarios RCP 8.5 Testing each forcing variable by replacing projection with climatology (historical average)

Mean distribution of skipjack larvae Climate change projections

Perspectives: Climate Change Ensemble simulations with more simulations Simulations at higher resolution (Matear et al 2015: Deep-Sea Research II 113: 22 46) Test ocean acidification impact Two examples of introducing ph effect through functional relationships in the modeling of early life history of tuna With the financial support from the New Zealand Ministry for Foreign Affairs and Trade, the Principality of Monaco (The Pacific Islands Partnership on Ocean Acidification Project) and the Global Environment Facility (Oceanic Fisheries Management Project II). a) Assuming lower ph has an energetic cost (requiring higher prey density). b) Introducing a more general functional relationship between ph and favorability in the definition of the spawning habitat index.

Perspectives: Other Species Other species: YFT BET ALB SWO Ongoing update for yellowfin and bigeye tuna using

Perspectives: Operational INDESO: INfrastructure DEvelopment for Space Oceanography (2013-17) INDESO project for the Gov. of Indonesia (Balitbang KP: Research & Development Agency of the Indonesian Ministry of Fisheries and Marine Affairs), with support of French Agency for Development, includes the development of an operational configuration of SEAPODYM to provide real-time and forecast of SKJ, YFT and BET pop. Dynamics in the Indonesian region. http://www.indeso.web.id/indeso_wp/index.php

Perspectives: Operational To provide initial and boundary conditions to the high resolution regional model at 1/12 x day, a global model at resolution of ¼ x week has been developed. Realtime and 2-week forecast are generated each week. Basin scale optimization conducted with SPC are used to update the system. http://www.indeso.web.id/indeso_wp/index.php Total skipjack tuna density

Perspectives: Operational The final objective is to use real time catch and effort information in the system rather than the average fishing effort based on the last few years, using Electronic Reporting System (ERS) or /and Vessel Monitoring Systems (VMS). Longliner VMS data Setting Soak time Hauling Data mining techniques to detect regular patterns without any prior information are used to get accurate estimates of fishing effort