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resumen

Resumen
The lack of planning regarding the spatial location and extent of different anthropogenic activities (such as agricultural production, biodiversity conservation, tourism, and urbanization) results in unsustainable land use and occupancy. Unplanned land use change threatens the supply of ecosystem services (ES) and thus, human well-being. Reversing this requires participatory land use planning that includes the stakeholders who inhabit the territory. Here, [ver mas...]
dc.contributor.authorAhumada, María Luján
dc.contributor.authorCavallero, Laura
dc.contributor.authorEasdale, Marcos Horacio
dc.contributor.authorTittonell, Pablo Adrian
dc.contributor.authorLopez, Dardo Ruben
dc.date.accessioned2025-01-10T10:07:48Z
dc.date.available2025-01-10T10:07:48Z
dc.date.issued2024-12-26
dc.identifier.citationAhumada, Maria Lujan; Cavallero, Laura; Easdale, Marcos Horacio; Tittonell, Pablo; López, Dardo Rubén; Mapping Ecosystem Conservation Priority Based on Social Assessment, a Tool to Assist Land Use Planning; John Wiley & Sons Ltd; Land Degradation & Development; 11-2024; 1-24es_AR
dc.identifier.issn1085-3278
dc.identifier.issn1099-145X
dc.identifier.otherhttps://doi.org/10.1002/ldr.5391
dc.identifier.urihttp://hdl.handle.net/20.500.12123/20933
dc.identifier.urihttps://onlinelibrary.wiley.com/doi/10.1002/ldr.5391
dc.description.abstractThe lack of planning regarding the spatial location and extent of different anthropogenic activities (such as agricultural production, biodiversity conservation, tourism, and urbanization) results in unsustainable land use and occupancy. Unplanned land use change threatens the supply of ecosystem services (ES) and thus, human well-being. Reversing this requires participatory land use planning that includes the stakeholders who inhabit the territory. Here, we analyze the social assessment of ES and its spatial representation on a map of Ecosystem Conservation Priority (ECP). In participatory workshops, we used the Analytic Hierarchy Process to characterize the assessment of stakeholders about the ES provided by forest landscapes. Among the ES analyzed, all stakeholders prioritized ES associated with hydrological regulation (Watershed Conservation Potential). Most stakeholders assigned a lower value to provisioning ES than to supporting and regulating ES, except for Agribusiness and Farmers. In addittion, we integrated social assessments with spatially explicit information through Multicriteria Modeling which allowed us to map ECP. Finally, we generated a map of consensus and dissent regarding ECP which can be used as input for land use planning. The highest consensus levels (86.45%) were mainly located in the upper watershed. In contrast, lower consensus levels (7.88%) were located mainly in plain areas of degraded and fragmented native forests. These results suggest that the ongoing transformation of forest ecosystems is linked to tensions that prioritize urbanization and agricultural activities as opposed to agroforestry land uses. Efforts to prevent the degradation of natural ecosystems require planning that addresses the complexity of social-ecological systems.eng
dc.formatapplication/pdfes_AR
dc.language.isoenges_AR
dc.publisherWileyes_AR
dc.relationinfo:eu-repograntAgreement/INTA/2019-RIST-E1-I027-001, Red de agroecologíaes_AR
dc.rightsinfo:eu-repo/semantics/restrictedAccesses_AR
dc.rights.urihttp://creativecommons.org/licenses/by-nc-sa/4.0/es_AR
dc.sourceLand Degradation & Development : 1-24 (First published: 24 November 2024)es_AR
dc.subjectServicios de los Ecosistemases_AR
dc.subjectEcosystem Serviceseng
dc.subjectParticipación Sociales_AR
dc.subjectSocial Participationeng
dc.subjectForestaciónes_AR
dc.subjectForestationeng
dc.titleMapping Ecosystem Conservation Priority Based on Social Assessment, a Tool to Assist Land Use Planninges_AR
dc.typeinfo:ar-repo/semantics/artículoes_AR
dc.typeinfo:eu-repo/semantics/articlees_AR
dc.typeinfo:eu-repo/semantics/publishedVersiones_AR
dc.rights.licenseCreative Commons Attribution-NonCommercial-ShareAlike 4.0 International (CC BY-NC-SA 4.0)es_AR
dc.description.origenEEA Manfredies_AR
dc.description.filFil: Ahumada, Maria Lujan. Instituto Nacional de Tecnología Agropecuaria (INTA). Estación Experimental Agropecuaria Manfredi. Estación Forestal Villa Dolores; Argentina. Consejo Nacional de Investigaciones Científicas y Técnicas. Centro Científico Tecnológico Conicet - Córdoba; Argentinaes_AR
dc.description.filFil: Cavallero, Laura. Instituto Nacional de Tecnología Agropecuaria (INTA). Estación Experimental Agropecuaria Manfredi. Estación Forestal Villa Dolores; Argentina. Consejo Nacional de Investigaciones Científicas y Técnicas. Centro Científico Tecnológico Conicet - Córdoba; Argentinaes_AR
dc.description.filFil: Easdale, Marcos Horacio. Instituto Nacional de Tecnología Agropecuaria (INTA). Estación Experimental Agropecuaria Bariloche. Instituto de Investigaciones Forestales y Agropecuarias Bariloche. - Consejo Nacional de Investigaciones Científicas y Técnicas. Centro Científico Tecnológico Conicet - Patagonia Norte. Instituto de Investigaciones Forestales y Agropecuarias Bariloche; Argentinaes_AR
dc.description.filFil: Tittonell, Pablo. Instituto Nacional de Tecnología Agropecuaria (INTA). Estación Experimental Agropecuaria Bariloche. Instituto de Investigaciones Forestales y Agropecuarias Bariloche. - Consejo Nacional de Investigaciones Científicas y Técnicas. Centro Científico Tecnológico Conicet - Patagonia Norte. Instituto de Investigaciones Forestales y Agropecuarias Bariloche; Argentinaes_AR
dc.description.filFil: López, Dardo Rubén. Instituto Nacional de Tecnología Agropecuaria (INTA). Estación Experimental Agropecuaria Manfredi. Estación Forestal Villa Dolores; Argentinaes_AR
dc.subtypecientifico


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