TY - JOUR
T1 - Global manta and devil ray population declines: closing policy and management gaps to reduce fisheries mortality
AU - Laglbauer, Betty J.L.
AU - D'Costa, Nidhi G.
AU - Stewart, Joshua D.
AU - Palacios, Marta D.
AU - Cronin, Melissa
AU - Fernando, Daniel
AU - Lezama-Ochoa, Nerea
AU - Armstrong, Asia O.
AU - Jabado, Rima W.
AU - Fowler, Sarah
AU - Lawson, Julia M.
AU - Koubrak, Olga
AU - Murua, Jefferson
AU - Ko Gyi, Thanda
AU - Karnad, Divya
AU - Chopra, Mayuri
AU - Notarbartolo-Di-Sciara, Giuseppe
AU - Rambahiniarison, Joshua
AU - Croll, Don
AU - Rojas, Stefany
AU - Fahmi, Abdulaziz
AU - Harris, Joanna L.
AU - Binthe Haque, Alifa
AU - Murua, Hilario
AU - Pérez-Jiménez, Juan Carlos
AU - Humble, Emily
AU - Barrowclift, Ellen
AU - Salim, Muhammad G.
AU - De Bruyne, Godefroy
AU - Seidu, Issah
AU - Zambrano-Vizquel, Luis A.
AU - Davies, Katrina
AU - Moazzam Khan, Muhammad
AU - Bucair, Nayara
AU - Johnson, Jeannie
AU - Labyedh, Ghofrane
AU - Takoukam Kamla, Aristide
AU - Fuentes, Karen
AU - Carter, Rebecca
AU - Barros, Nuno
AU - Stevens, Guy M.W.
PY - 2025/11/7
Y1 - 2025/11/7
N2 - Significant progress has been made in advancing priority actions to conserve manta and devil rays, yet implementation and enforcement of protective measures often fall short, leaving most mobulid populations at risk of overfishing. Drawing on a literature review, fisheries databases, agency reports, and expert interviews, we assess global trends in mobulid catch and mortality. We examine both targeted and incidental catch, in small (<15 m, ‘SV’) and large (>15 m, ‘LV’) vessel fisheries to identify hotspots with the highest risk of fisheries-related mortality and population decline. We estimate global fisheries catch at 264,520 (184,407–344,987) mobulids per year, with SV fisheries accounting for 87 % of global mortality. The highest-risk hotspots, based on mortality and declines, are located in India, Indonesia, Sri Lanka, Peru, and Myanmar. Mobulid retention is driven by demand, with higher mortality rates observed in countries exporting gill plates, and to a lesser extent, in those trading meat domestically or internationally. We recommend urgent implementation and enforcement of mobulid listings under the Convention on International Trade in Endangered Wild Flora and Fauna (CITES), the Convention on the Conservation of Migratory Species of Wild Animals (CMS), and national protective measures, including (i) uplisting mobulids to CITES Appendix I, (ii) full legislative protection for all mobulid species in high-risk fishing nations to reduce demand, (iii) avoiding fishing in critical habitats through permanent or temporary targeted area closures, or management, (iv) limiting drift gillnet effort, and (v) involving fishers in management decisions and implementation.
AB - Significant progress has been made in advancing priority actions to conserve manta and devil rays, yet implementation and enforcement of protective measures often fall short, leaving most mobulid populations at risk of overfishing. Drawing on a literature review, fisheries databases, agency reports, and expert interviews, we assess global trends in mobulid catch and mortality. We examine both targeted and incidental catch, in small (<15 m, ‘SV’) and large (>15 m, ‘LV’) vessel fisheries to identify hotspots with the highest risk of fisheries-related mortality and population decline. We estimate global fisheries catch at 264,520 (184,407–344,987) mobulids per year, with SV fisheries accounting for 87 % of global mortality. The highest-risk hotspots, based on mortality and declines, are located in India, Indonesia, Sri Lanka, Peru, and Myanmar. Mobulid retention is driven by demand, with higher mortality rates observed in countries exporting gill plates, and to a lesser extent, in those trading meat domestically or internationally. We recommend urgent implementation and enforcement of mobulid listings under the Convention on International Trade in Endangered Wild Flora and Fauna (CITES), the Convention on the Conservation of Migratory Species of Wild Animals (CMS), and national protective measures, including (i) uplisting mobulids to CITES Appendix I, (ii) full legislative protection for all mobulid species in high-risk fishing nations to reduce demand, (iii) avoiding fishing in critical habitats through permanent or temporary targeted area closures, or management, (iv) limiting drift gillnet effort, and (v) involving fishers in management decisions and implementation.
KW - At-vessel mortality
KW - CITES
KW - Catch
KW - Elasmobranch
KW - Landings
KW - Mobulid ray
UR - https://pearl.plymouth.ac.uk/bms-research/2267/
U2 - 10.1016/j.biocon.2025.111589
DO - 10.1016/j.biocon.2025.111589
M3 - Article
SN - 0006-3207
VL - 313
JO - Biological Conservation
JF - Biological Conservation
M1 - 111589
ER -