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dc.contributor.authorMosquera-Guerra, F.
dc.contributor.authorTrujillo, F.
dc.contributor.authorOliveira-da-Costa, M.
dc.contributor.authorMarmontel, M.
dc.contributor.authorVan Damme, P.A.
dc.contributor.authorFranco, N.
dc.contributor.authorCórdova, L.
dc.contributor.authorCampbell, E.
dc.contributor.authorAlfaro-Shigueto, J.
dc.contributor.authorMena, J.L.
dc.contributor.authorMangel, J.C.
dc.contributor.authorOviedo, J.S.U.
dc.contributor.authorCarvajal-Castro, J.D.
dc.contributor.authorMantilla-Meluk, H.
dc.contributor.authorArmenteras-Pascual, D.
dc.date.accessioned2025-10-31T18:34:02Z
dc.date.available2025-10-31T18:34:02Z
dc.date.issued2021
dc.identifier.urihttps://hdl.handle.net/20.500.12805/5059
dc.description.abstractStudying the variables that describe the spatial ecology of threatened species allows us to identify and prioritize areas that are critical for species conservation. To estimate the home range and core area of the Endangered (EN) Amazon river dolphin Inia geoffrensis, 23 individuals (6f, 17m) were tagged during the rising water period in the Amazon and Orinoco river basins between 2017 and 2018. The satellite tracking period ranged from 24 to 336 d (mean ± SE = 107 ± 15.7 d), and river dolphin movements ranged from 7.5 to 298 km (58 ± 13.4 km). Kernel density estimates were used to determine minimum home ranges at 95% (K<inf>95</inf> = 6.2 to 233.9 km2; mean = 59 ± 13.5 km2) and core areas at 50% (K<inf>50</inf> = 0.6 to 54.9 km2; mean = 9 ± 2.6 km2). Protected areas accounted for 45% of the K<inf>50</inf> estimated core area. We observed dolphin individuals crossing country borders between Colombia and Peru in the Amazon basin, and between Colombia and Venezuela in the Orinoco basin. Satellite tracking allowed us to determine the different uses of riverine habitat types: main rivers (channels and bays, 52% of recorded locations), confluences (32%), lagoons (9.6%), and tributaries (6.2%). Satellite monitoring allowed us to better understand the ecological preferences of the species and demonstrated the importance of maintaining aquatic landscape heterogeneity and spatial connectivity for effective river dolphin conservation.en_US
dc.description.sponsorshipAcknowledgements. This program is part of the strategic plan set by the South American River Dolphin Initiative (SARDI), supported by World Wildlife Fund (WWF) in Brazil, Colombia, Peru, Ecuador, and Bolivia. Partial support for 2 tags in Peru was provided by the Rufford Foundation through RSG. Special gratitude to D. Amorocho, D. Willems, K. Berg, L. Sainz, J. Rivas, J. Surkin, R. Maldonado, D. Ember, V. Tellez, H. Yagui, N. Acu\u00F1a, P. Colchao, M. Pajuelo, F. Nishio, and M. Wulms from WWF, and D. Parks from the Whitley Fund for Nature (WFN). F.M.G. received a doctoral scholarship from Colciencias (National Doctorate Scholarship 785 to 2017). E.C. received a doctoral scholarship from WWF-EFN. A. Echeverr\u00EDa and A. Salinas are acknowledged for their support during tagging campaigns in Bolivia. We acknowledge the fishing communities and the local and national authorities for participating in the river dolphin capture process.
dc.formatapplication/pdf
dc.language.isoeng
dc.publisherInter-Research
dc.relation.ispartofurn:issn:1613-4796
dc.rightshttps://purl.org/coar/access_right/c_abf2
dc.rights.urihttps://creativecommons.org/licenses/by-nc-sa/4.0/
dc.subjectSDG 15en_US
dc.subjectAcoustic Monitoring of Marine Mammal Populationsen_US
dc.subjectConservation and Ecology of Amazon River Dolphinsen_US
dc.titleHome range and movements of Amazon river dolphins Inia geoffrensisin the Amazon and Orinoco river basinsen_US
dc.typehttps://purl.org/coar/resource_type/c_2df8fbb1
dc.identifier.doihttps://doi.org/10.3354/esr01133
dc.subject.ocdehttps://purl.org/pe-repo/ocde/ford#1.06.13
dc.type.otherResearch article
dc.identifier.journalEndangered Species Research
dc.type.versionhttps://purl.org/coar/version/c_970fb48d4fbd8a85


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