Please use this identifier to cite or link to this item: http://hdl.handle.net/10553/129597
DC FieldValueLanguage
dc.contributor.authorCruces, Lorenzoen_US
dc.contributor.authorRodríguez, Myriamen_US
dc.contributor.authorMonterroso, Óscaren_US
dc.contributor.authorÁlvarez, Omaren_US
dc.contributor.authorPérez, Óscaren_US
dc.contributor.authorRiera, Rodrigoen_US
dc.date.accessioned2024-03-21T13:32:20Z-
dc.date.available2024-03-21T13:32:20Z-
dc.date.issued2024en_US
dc.identifier.issn1052-7613en_US
dc.identifier.otherScopus-
dc.identifier.urihttp://hdl.handle.net/10553/129597-
dc.description.abstractThis study analysed the catches of trap fishing in the Canary Archipelago, NE Atlantic Ocean. This study was conducted from October 2016 to September 2017, April to November 2018 and September 2020, in five ports (San Cristóbal, Taliarte, Castillo del Romeral, Arguineguín and Mogán). The primary gear were traps with small mesh size (31.6 mm) and large mesh size (50.8 mm). A total of 2587 small mesh size traps and 141 large mesh size traps were analysed from 20- to 130-m depth. The main target species were Dentex gibbosus and Stephanolepis hispidus. Catches of traps with large mesh size showed D. gibbosus above first maturity and S. hispidus in small mesh size traps. Both species exhibit larger specimens during reproductive periods. The most effective traps for D. gibbosus (large mesh) were located on the western coast (>30-m depth), with the highest catch per unit of effort (CPUE) in Mogán (857.7 g trap−1 day−1). The most effective traps for S. hispidus (small mesh) were located in southern areas, especially in sandy habitats (124.9 g trap−1 day−1 in Castillo del Romeral, 102.9 g trap−1 day−1 in Arguineguín). The highest catchability of D. gibbosus was observed in April (CPUE of 962.8 g trap−1 day−1), and the highest catchability of S. hispidus was found in June (CPUE of 165.9 g trap−1 day−1). The traps with small mesh size showed a great selectivity of sizes for S. hispidus; though high catch rates of immature specimens of D. gibbosus pose a threat to species conservation. The management recommendations' proposed measures include revising minimum catch sizes for both species. Additionally, we suggested depth limitations for mesh sizes of traps. The study highlights the need for new management strategies to ensure the conservation of targeted demersal species, with special emphasis on addressing the threat posed by small mesh sizes to immature D. gibbosus. The findings provide valuable insights for adapting fishery management practices to sustainably conserve the targeted species in the Canary Archipelago.en_US
dc.languageengen_US
dc.relation.ispartofAquatic Conservation: Marine and Freshwater Ecosystemsen_US
dc.sourceAquatic Conservation: Marine and Freshwater Ecosystems [ISSN 1052-7613],v. 34 (3)en_US
dc.subject531201 Agricultura, silvicultura, pescaen_US
dc.subject310506 Técnicas pesquerasen_US
dc.subject310504 Protección de los pecesen_US
dc.subject.otherArtisanal fisheryen_US
dc.subject.otherCommercial fishen_US
dc.subject.otherDentex gibbosusen_US
dc.subject.otherGran Canariaen_US
dc.subject.otherNe Atlantic Oceanen_US
dc.subject.otherStephanolepis hispidusen_US
dc.titleSpatial and temporal variability of the two main catched species of an artisanal trap fishery in an oceanic islanden_US
dc.typeinfo:eu-repo/semantics/Articleen_US
dc.typeArticleen_US
dc.rights.licenseBY-NC-ND-
dc.identifier.doi10.1002/aqc.4090en_US
dc.identifier.scopus85187120128-
dc.identifier.isi001182222300001-
dc.contributor.orcidNO DATA-
dc.contributor.orcidNO DATA-
dc.contributor.orcidNO DATA-
dc.contributor.orcidNO DATA-
dc.contributor.orcidNO DATA-
dc.contributor.orcid0000-0003-1264-1625-
dc.contributor.authorscopusid57219114043-
dc.contributor.authorscopusid37113003500-
dc.contributor.authorscopusid8970659100-
dc.contributor.authorscopusid57055257000-
dc.contributor.authorscopusid7005049167-
dc.contributor.authorscopusid7003416980-
dc.identifier.eissn1099-0755-
dc.identifier.issue3-
dc.relation.volume34en_US
dc.investigacionCienciasen_US
dc.type2Artículoen_US
dc.contributor.daisngid20625302-
dc.contributor.daisngid13261057-
dc.contributor.daisngid12252953-
dc.contributor.daisngid55888837-
dc.contributor.daisngid39068413-
dc.contributor.daisngid55932323-
dc.description.numberofpages11en_US
dc.utils.revisionen_US
dc.contributor.wosstandardWOS:Cruces, L-
dc.contributor.wosstandardWOS:Rodriguez, M-
dc.contributor.wosstandardWOS:Monterroso, O-
dc.contributor.wosstandardWOS:Alvarez, O-
dc.contributor.wosstandardWOS:Perez, O-
dc.contributor.wosstandardWOS:Riera, R-
dc.date.coverdateMarzo 2024en_US
dc.identifier.ulpgcen_US
dc.contributor.buulpgcBU-BASen_US
dc.description.sjr0,787-
dc.description.jcr2,4-
dc.description.sjrqQ1-
dc.description.jcrqQ2-
dc.description.scieSCIE-
dc.description.miaricds11,0-
item.grantfulltextopen-
item.fulltextCon texto completo-
crisitem.author.deptGIR ECOAQUA: Biodiversidad y Conservación-
crisitem.author.deptIU de Investigación en Acuicultura Sostenible y Ec-
crisitem.author.deptDepartamento de Biología-
crisitem.author.orcid0000-0003-1264-1625-
crisitem.author.parentorgIU de Investigación en Acuicultura Sostenible y Ec-
crisitem.author.fullNameRiera Elena, Rodrigo-
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