Abstract
Marine ecosystems, biodiversity, and fisheries are under strain worldwide due to global changes including climate warming and demographic pressure. To address this issue, many scientists and stakeholders advocate the use of an ecosystem approach for fisheries that integrates the numerous ecological and economic complexities at play rather than focusing on the management of individual target species. However, the operationalization of such an ecosystem approach remains challenging, especially from a bio-economic standpoint. Here, to address this issue, we propose a model of intermediate complexity (MICE) relying on multi-species, multi-fleet, and resource-based dynamics. Climate change effects are incorporated through an envelope model for the biological growth of fish species as a function of sea surface temperature. The model is calibrated for the small-scale fishery in French Guiana using a time series of fish landings and fishing effort from 2006 to 2018. From the calibrated model, a predictive fishing effort projection and RCP climate scenarios derived from IPCC, we explore the ecosystem dynamics and the fishery production at the horizon 2100. Our results demonstrate the long-term detrimental impact of both climate change and ecological competition on fish biodiversity. The prognosis is particularly catastrophic under the most pessimistic climate scenario, with a potential collapse of both biomass targeted species and fishing activity by 2100.
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Availability of data and material
Data of fishing landings and efforts are available in the website of the IFREMER Fisheries Information System (https://sih.ifremer.fr/). Observed sea surface temperature data (SST) are extracted from the NOAA Earth System Research Laboratory website (https://www.esrl.noaa.gov/).
Code availability
This study has been performed thanks to the scientific software SCILAB. In particular the calibration was done with “optim_ga” routine. The numerical codes for the calibration and the scenarios are available in the Google drive of codes.enmo.d.20.00261@gmail.com, password: ENMO.D.20.00261. Please contact Hélène Gomes in case of any problem.
Notes
Using data on fish landings for a given effort as well as comprehensive data on fishing effort, IFREMER observers are able to extrapolate landings for all boats and landing points on a quarterly basis using the rule of three. During this period, the fishermen made no technical adaptations and installed no new equipment that would have increased fishing power. Therefore, we can assume that the efficiency of the French Guiana fishery remains constant over time.
In the model proposed for the French Guiana fishery by Cissé et al. [42], trophic interactions turn out to have a weak influence. Here, we have simplified the model by ignoring trophic interactions between fishes in order to focus on the influence of the environment on population dynamics.
However we are aware that a longer timeframe introduces significant additional uncertainties to the model.
We used the level of the resource stock at equilibrium in year 2085 to obtain \(B_{res,i}^*\)
$$B_{res,i}^*=\frac{M_i+\displaystyle {\sum _{f=1}^{F}}q_{i,f}E_f(t_{2085})}{\gamma _i\big (\theta (t_{2085}-\tau _i)\big )g_i a_{res,i}},$$with \(t_{2085}\) corresponding to the value of the first quarter of the year 2085. The choice of the year 2085 is rather arbitrary. The idea is to consider a relatively distant year in which two species would already be extinct.
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Funding
This study, including data collection and analyzes, was funded by the IFREMER (Institut Français de Recherche pour l’Exploitation de la Mer; english: French Research Institute for Exploitation of the Sea). It also benefited from the CNRS research project entitled ENTROPIC (Ecological-ecoNomic resilience of TROPIcal coastal eCosystem).
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All authors contributed to the study conception and design. The model was developed by Abdoul Ahad Cissé, Luc Doyen, Hélène Gomes and Coralie Kersulec. Scenarios for the projections were performed by Luc Doyen and Nicolas Sanz. Analysis were conducted by Fabian Blanchard and Hélène Gomes. The first draft was written by Hélène Gomes and all authors commented on previous versions of the manuscript. All authors read and approved the final manuscript.
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Appendix
Appendix
1.1 Geographic Coordinates of the Points used for the SST
See Table 7.
1.2 Temperatures \(\theta _{i,10}\) , \(\theta _{i,opt}\), \(\theta _{i,90}\) used for Climate Change Modelling
See Table 8
1.3 Rate \(\delta ^{hist}_f\) used for Projected Efforts
See Table 9.
1.4 Sensitivity Analysis
A sensitivity analysis was carried out to evaluate reliability and contribution to the outputs for each calibrated parameter. To this end, additional simulations were run based on the PS, RCP 2.6, and RCP 8.5 scenarios. Due to the large number of parameters, we simplified the sensitivity analysis for each climate scenario by simultaneously perturbing all of the calibrated parameters of the same category. There were seven categories in total: trophic interactions, catchability, mortality rate, growth efficiency, initial biomass, time lag, and values of I. For each category of parameters, a level of noise ranging from -10% to +10% of the calibrated values was added. Relative differences in average catch per quarter \(\bar{H}=\frac{1}{t_f-t_1} \sum _{t=t_1}^{t_f}\sum _{f=1}^{F}\sum _{i=1}^{N}H_{i,f}(t)\) were computed for each climate scenario.
Figure 11 displays the sensitivity results for both climate scenarios. These results show that the parameters with the greatest impact, in both cases, are catchability, mortality, growth efficiency, and values of I. With the exception of the time-lag parameter, the relative change in average catch appears to vary more or less linearly with the magnitude of the perturbations, with the absolute value of the slopes ranging from 0.008 to 0.97, indicating the bounds of the marginal effects of the parameters. Since the relative changes are smaller than the magnitude of the perturbations for these parameters, it appears that the effects of these parameters are small. We can see that the impact of the perturbations on trophic interactions, growth efficiency, initial biomass, and parameter I is similar for both climate scenarios: the red and blue lines practically coincide. For the perturbations of the time lag, the graph of the relative change in catch is stepped; time lag is an integer value, so the magnitude of the perturbation has an impact when its value is higher than 1. Finally, we can see that the time lag has a greater effect on relative change in average catch in the RCP 8.5 scenario than in the RCP 2.6 scenario. This is because the temperature increase \(\Delta _{\omega ,t_f}\) is higher under RCP 8.5 than under RCP 2.6.
1.5 Comparison of Historical and Estimated CPUE
As the efficiency of the fishing time of the French Guiana coastal fishery is assumed to be constant between 2006 and 2018, the catch per unit effort (CPUE) can be considered a proxy for abundance [61]. Since ours is a multi-species, multi-fleet model, we cannot calculate the CPUE for each species. However, we can compute the CPUE for each fleet and for the aggregated catch. Figure 12 compares historical CPUE with the estimated CPUE. The position of the crosses on the diagonal suggests a satisfactory goodness-of-fit for every biomass.
1.6 Sea Surface Temperatures at Extinctions Dates of Each Species for Both Climate Scenario
See Table 10.
1.7 Biological Efficiency for the 13 Most-fished Species in the Coastal Fishery in French Guiana.
See Fig. 13
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Gomes, H., Kersulec, C., Doyen, L. et al. The Major Roles of Climate Warming and Ecological Competition in the Small-scale Coastal Fishery in French Guiana. Environ Model Assess 26, 655–675 (2021). https://doi.org/10.1007/s10666-021-09772-8
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DOI: https://doi.org/10.1007/s10666-021-09772-8