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Planning connectivity at multiple scales for large mammals in a human-dominated biodiversity hotspot
Institution:1. Wildlife Conservation Research Unit (WildCRU), Department of Zoology, University of Oxford, Recanati-Kaplan Centre, Tubney House, Tubney OX13 5QL, UK;2. US Forest Service, Rocky Mountain Research Station, 2500 S Pine Knoll Dr, Flagstaff, AZ 86001, USA;3. Danau Girang Field Centre, c/o Sabah Wildlife Department, Wisma Muis, 88100 Kota Kinabalu, Sabah, Malaysia;4. Sabah Wildlife Department, Wisma Muis, 88100 Kota Kinabalu, Sabah, Malaysia;5. Organisms and Environment Division, School of Biosciences, Cardiff University, Sir Martin Evans Building, Museum Avenue, Cardiff CF10 3AX, UK;6. Sustainable Places Research Institute, Cardiff University, 33 Park Place, Cardiff CF10 3BA, UK;7. Panthera, New York, NY, USA;8. Living Landscape Alliance, 110 Maui Court, Waikiki Condominium, Jalan Aru, Tanjung Aru, 88100 Kota Kinabalu, Sabah, Malaysia;9. ARC Centre of Excellence for Environmental Decisions, University of Queensland, Brisbane QLD 4072, Australia;1. Programa de Pós-graduação em Ecologia e Evolução, Universidade Federal de Goiás, CP 131, Goiás, GO 74001-970, Brazil;2. Programa de Pós-graduação Ciência para o Desenvolvimento, Instituto Gulbenkian de Ciências, Apartado 14, 2781-901 Oeiras, Portugal;3. Laboratório de Biogeografia da Conservação, Departamento de Ecologia, Universidade Federal de Goiás, CP 131, Goiás, GO 74001-970, Brazil;4. Universidade Eduardo Mondlane, Caixa Postal 75, Inhambane, Mozambique;5. Brazilian Research Network on Global Climate Change – Rede Clima, Instituto Nacional de Pesquisas Espaciais, São José dos Campos, São Paulo, Brazil
Abstract:Connectivity for large mammals across human-altered landscapes results from movement by individuals that can be described via nested spatial scales as linkages (or zones or areas) with compatible land use types, constrictions that repeatedly funnel movement (as corridors) or impede it (as barriers), and the specific paths (or routes) across completely anthropogenic features (such as highways). Mitigation to facilitate animal movement through such landscapes requires similar attention to spatial scale, particularly when they involve complex topography, diverse types of human land use, and transportation infrastructure. We modeled connectivity for Asian elephant (Elephas maximus) and gaur (Bos gaurus) in the Shencottah Gap, a multiple-use region separating two tiger reserves in the Western Ghats, India. Using 840 km of surveys for animal signs within a region of 621 km2, we modeled landscape linkages via resource selection functions integrated across two spatial resolutions, and then potential dispersal corridors within these linkages using circuit theoretical models. Within these corridors, we further identified potential small-scale movement paths across a busy transportation route via least-cost paths and evaluated their viability. Both elephants and gaur avoided human-dominated habitat, resulting in broken connectivity across the Shencottah Gap. Predicted corridor locations were sensitive to analysis resolution, and corridors derived from scale-integrated habitat models correlated best with habitat quality. Less than 1% of elephant and gaur detections occurred in habitat that was poorer in quality than the lowest-quality component of the movement path across the transportation route, suggesting that connectivity will require habitat improvement. Only 28% of dispersal corridor area and 5% of movement path length overlapped with the upper 50% quantile of the landscape linkage; thus, jointly modeling these three components enabled a more nuanced evaluation of connectivity than any of them in isolation.
Keywords:Corridor  Connectivity  Western Ghats  Landscape linkage  Elephant  Gaur  Tiger Reserve  Shencottah Gap
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