Dynamics of killer whale, bluefin tuna and human fisheries in the Strait of Gibraltar

A complex balance has arisen between the bluefin tuna, killer whales, and human activities in the Strait of Gibraltar. Recent changes in fishing effort have dramatically decreased tuna stocks, breaking this balance. Killer whales exhibit two strategies for feeding on tuna: active hunting and depreda...

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Bibliographic Details
Published in:Biological Conservation
Main Authors: Esteban, Ruth, Verborgh, Philippe, Gauffier, Pauline, Giménez, Joan, Guinet, Christophe, de Stephanis, Renaud
Other Authors: Ministerio de Economía y Competitividad (España), CEPSA, Loro Parque Fundación, Ministerio de Medio Ambiente (España), Fundación Biodiversidad
Format: Article in Journal/Newspaper
Language:unknown
Published: Elsevier 2016
Subjects:
Online Access:http://hdl.handle.net/10261/195980
https://doi.org/10.1016/j.biocon.2015.11.031
https://doi.org/10.13039/501100003329
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Summary:A complex balance has arisen between the bluefin tuna, killer whales, and human activities in the Strait of Gibraltar. Recent changes in fishing effort have dramatically decreased tuna stocks, breaking this balance. Killer whales exhibit two strategies for feeding on tuna: active hunting and depredation on a drop-line fishery. From 1999 to 2011, a small community of 39 individuals was observed in the Strait in spring and summer. All individuals displayed active hunting and 18 of themalso depredated on the fishery. These differences in foraging behaviour influenced life-history parameters. Adult survival for interacting and non-interacting individuals was estimated at 0.991 (SE=0.011) and 0.901 (SE=0.050), respectively. Juvenile survival could only be estimated for interacting individuals as 0.966 (SE = 0.024), because only one juvenile and one calf were observed among non-interacting individuals. None of the interacting calves survived after 2005, following the decrease in drop-line fishery catches. Calving rate was estimated at 0.22 (SE = 0.02) for interacting individuals and 0.02 (SE = 0.01) for non-interacting. Calving interval, which could only be calculated for interacting groups, was 7 years. The population growth rate was positive at 4% for interacting individuals, and no growth was observed for non-interacting individuals. These differences in demographic parameters could be explained by access to larger tuna through depredation. Consequently, we found that whales would need more tuna to cover their daily energy requirementswhile actively hunting. Therefore, our findings suggest an effect of artificial food provisioning on their survival and reproductive output. Urgent actions are needed to ensure the conservation of this, already small, community of killer whales. These include its declaration as Endangered, the implementation of a conservation plan, the creation of a seasonal management area where activities producing underwater noise (i.e. military exercise, seismic surveys or evenwhale watching ...