Problems with combining modelling and social science approaches to understand artisanal fisheries bycatch

dc.contributor.authorD. A. Villar
dc.contributor.authorEdwin R. Gutiérrez Tito
dc.contributor.authorPaola Velásquez‐Noriega
dc.contributor.authorAnahi Cosky Paca‐Condori
dc.contributor.authorEdmundo G. Moreno Terrazas
dc.contributor.authorAlfredo Balcón Cuno
dc.contributor.authorRonald Hinojosa Cárdenas
dc.contributor.authorCarmen Villanueva
dc.contributor.authorPatrick F. Chapman
dc.contributor.authorLuca Chiaverini
dc.coverage.spatialBolivia
dc.date.accessioned2026-03-22T15:18:53Z
dc.date.available2026-03-22T15:18:53Z
dc.date.issued2024
dc.descriptionCitaciones: 3
dc.description.abstractAbstract Aim Artisanal fisheries account for 40% of the world's fisheries catch, yet its environmental impacts remain poorly understood. This is especially the case in developing countries. In this study, we sought to integrate Local Fisher's Knowledge with distribution modelling to estimate the annual bycatch of Titicaca Grebe ( Rollandia microptera ), an endangered endemic bird from Lake Titicaca whose main anthropogenic threat is bycatch. Location Lake Titicaca, Peru and Bolivia. Methods We conducted transect and point counts of fishing nets in March–September 2022 and conducted interviews with fishers across the Lake Titicaca region. Using bathymetry, distance from shore, distance from a settlement, distance from the protected area, presence/absence of aquaculture, distance from aquaculture, and wetland cover, we constructed a distribution model of fisheries using maximum entropy modelling. We conducted interviews with fishers asking about the frequency of grebe bycatch and conducted short‐term monitoring at various sites while conducting transect points for dead grebes. Results We estimate 3270 km 2 of the surface area of Lake Titicaca is used for fishing, which amounts to 39.40% of the lake's surface area. The area under the curve (AUC) of the distribution model was 0.89 and the True Skill Statistic was 0.67, which suggests maximum entropy modelling can model fisheries occurrence. The results of our interviews suggested a biologically implausible large number of grebes caught as bycatch annually. The cultural context of the interviews, including potential influences of non‐response and social‐desirability bias, being with fishers who often view the Titicaca Grebe as a nuisance species, might have caused over‐reporting of bycatch and hence led to these implausible figures. Main Conclusions It is possible to map fisheries using distribution models as one might with species. However, obtaining accurate measures of fisheries bycatch through interviews is more difficult, due to cultural factors which affect the accuracy in fisher's responses. While we hope that this method provides a low‐cost alternative to monitoring, it is not a suitable replacement for it.
dc.identifier.doi10.1111/ddi.13918
dc.identifier.urihttps://doi.org/10.1111/ddi.13918
dc.identifier.urihttps://andeanlibrary.org/handle/123456789/51645
dc.language.isoen
dc.publisherWiley
dc.relation.ispartofDiversity and Distributions
dc.sourceUniversity of Oxford
dc.subjectBycatch
dc.subjectGeography
dc.subjectFishery
dc.subjectFishing
dc.subjectTransect
dc.subjectEndangered species
dc.subjectContext (archaeology)
dc.subjectEcology
dc.titleProblems with combining modelling and social science approaches to understand artisanal fisheries bycatch
dc.typearticle

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