Where will the dhole survive in 2030? Predicted strongholds in mainland Southeast Asia

dc.contributor.authorTananantayot J.
dc.contributor.authorAgger C.
dc.contributor.authorAsh E.
dc.contributor.authorAung S.S.
dc.contributor.authorBaker-Whatton M.C.
dc.contributor.authorBisi F.
dc.contributor.authorClements G.R.
dc.contributor.authorCremonesi G.
dc.contributor.authorCrouthers R.
dc.contributor.authorFrechette J.L.
dc.contributor.authorGale G.A.
dc.contributor.authorGodfrey A.
dc.contributor.authorGray T.N.E.
dc.contributor.authorGreenspan E.
dc.contributor.authorGriffin O.
dc.contributor.authorGrindley M.
dc.contributor.authorHashim A.K.B.A.
dc.contributor.authorJenks K.E.
dc.contributor.authorSay K'lu S.
dc.contributor.authorLam W.Y.
dc.contributor.authorLynam A.J.
dc.contributor.authorMcCann G.E.
dc.contributor.authorMohamad S.W.
dc.contributor.authorPetersen W.J.
dc.contributor.authorSivayogam C.P.
dc.contributor.authorRayan D.M.
dc.contributor.authorRiggio A.M.
dc.contributor.authorSaosoong S.
dc.contributor.authorSavini T.
dc.contributor.authorSeuaturien N.
dc.contributor.authorShwe N.M.
dc.contributor.authorSiripattaranukul K.
dc.contributor.authorSteinmetz R.
dc.contributor.authorSuksavate S.
dc.contributor.authorSukumal N.
dc.contributor.authorTantipisanuh N.
dc.contributor.authorVinitpornsawan S.
dc.contributor.authorNgoprasert D.
dc.contributor.otherMahidol University
dc.date.accessioned2023-06-18T17:14:38Z
dc.date.available2023-06-18T17:14:38Z
dc.date.issued2022-11-01
dc.description.abstractDhole (Cuon alpinus) is threatened with extinction across its range due to habitat loss and prey depletion. Despite this, no previous study has investigated the distribution and threat of the species at a regional scale. This lack of knowledge continues to impede conservation planning for the species. Here we modeled suitable habitat using presence-only camera trap data for dhole and dhole prey species in mainland Southeast Asia and assessed the threat level to dhole in this region using an expert-informed Bayesian Belief Network. We integrated prior information to identify dhole habitat strongholds that could support populations over the next 50 years. Our habitat suitability model identified forest cover and prey availability as the most influential factors affecting dhole occurrence. Similarly, our threat model predicted that forest loss and prey depletion were the greatest threats, followed by local hunting, non-timber forest product collection, and domestic dog incursion into the forest. These threats require proactive resource management, strong legal protection, and cross-sector collaboration. We predicted <20% of all remaining forest cover in our study area to be suitable for dhole. We then identified 17 patches of suitable forest area as potential strongholds. Among these patches, Western Forest Complex (Thailand) was identified as the region's only primary stronghold, while Taman Negara (Malaysia), and northeastern landscape (Cambodia) were identified as secondary strongholds. Although all 17 patches met our minimum size criteria (1667 km2), patches smaller than 3333 km2 may require site management either by increasing the ecological carrying capacity (i.e., prey abundance) or maintaining forest extent. Our proposed interventions for dhole would also strengthen the conservation of other co-occurring species facing similar threats. Our threat assessment technique of species with scarce information is likely replicable with other endangered species.
dc.identifier.citationConservation Science and Practice Vol.4 No.11 (2022)
dc.identifier.doi10.1111/csp2.12831
dc.identifier.eissn25784854
dc.identifier.scopus2-s2.0-85140065062
dc.identifier.urihttps://repository.li.mahidol.ac.th/handle/20.500.14594/84662
dc.rights.holderSCOPUS
dc.subjectEnvironmental Science
dc.titleWhere will the dhole survive in 2030? Predicted strongholds in mainland Southeast Asia
dc.typeArticle
mu.datasource.scopushttps://www.scopus.com/inward/record.uri?partnerID=HzOxMe3b&scp=85140065062&origin=inward
oaire.citation.issue11
oaire.citation.titleConservation Science and Practice
oaire.citation.volume4
oairecerif.author.affiliationFauna &amp; Flora International
oairecerif.author.affiliationPanthera USA
oairecerif.author.affiliationSunway University
oairecerif.author.affiliationFaculty of Environment and Resource Studies, Mahidol University
oairecerif.author.affiliationNational Park, Wildlife and Plant Conservation Department, Thailand
oairecerif.author.affiliationWWF Thailand
oairecerif.author.affiliationJabatan Perlindungan Hidupan Liar dan Taman Negara
oairecerif.author.affiliationWildlife Conservation Society Cambodia
oairecerif.author.affiliationUniversity of Oxford
oairecerif.author.affiliationConservation and Research Center (National Zoo)
oairecerif.author.affiliationKasetsart University
oairecerif.author.affiliationWildfowl and Wetlands Trust
oairecerif.author.affiliationChang Gung University
oairecerif.author.affiliationNature Conservancy
oairecerif.author.affiliationKing Mongkut's University of Technology Thonburi
oairecerif.author.affiliationUniversità degli Studi dell'Insubria
oairecerif.author.affiliationWildlife Conservation Society
oairecerif.author.affiliationJalan University
oairecerif.author.affiliationKawthoolei Forestry Department
oairecerif.author.affiliationKaren Wildlife Conservation Initiative
oairecerif.author.affiliationWWF Tigers Alive Initiative
oairecerif.author.affiliationRimba
oairecerif.author.affiliationWildlife Alliance
oairecerif.author.affiliationWWF-Cambodia
oairecerif.author.affiliationConservation International
oairecerif.author.affiliationIstituto Oikos Onlus
oairecerif.author.affiliationWWF Malaysia
oairecerif.author.affiliationWildlife Conservation Society

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