Affiliation: | 1. Departamento de Conservación de la Biodiversidad, El Colegio de la Frontera Sur, Av. Rancho Poligono 2-A, Ciudad Industrial, 24500 Lerma, Campeche, México;2. Fundación Yaguará Panamá, Ciudad del Saber, Edificio 101, Clayton, P.O. Box 0833-0292 Panama Smithsonian Tropical Research Institute, Luis Clement Avenue, Building 401 Tupper, Balboa Ancon, Postal 0843-03092 Panama;3. Department of Environmental Conservation, University of Massachusetts Amherst, Amherst, MA, 01003 U.S.A.;4. Bioconciencia A.C., Ocotepec L10 Mz 74 Esq. Poza Rica, Col. San Jerónimo Aculco, Del. Magdalena Contreras, C.P. 10400 Ciudad de México, Mexico;5. Smithsonian Tropical Research Institute, Luis Clement Avenue, Building 401 Tupper, Balboa Ancon, Postal 0843-03092 Panama;6. Global Wildlife Conservation, P.O. Box 129, Austin, TX, 78767 U.S.A.;7. Panthera, 8W 40th St, 18th Floor, New York, NY, 10018 U.S.A. Conservación Panamá Inc., calle via Tambo, Finca Radagast, Penonomé, Coclé, Panamá;8. Fundación Yaguará Panamá, Ciudad del Saber, Edificio 101, Clayton, P.O. Box 0833-0292 Panama;9. Biodiversity Consultant Group, Hato Pintado, 78 ½ St, L 13, Ciudad de Panamá, 33172-2780/GEL7200 Panama |
Abstract: | Habitat fragmentation is a primary driver of wildlife loss, and establishment of biological corridors is a common strategy to mitigate this problem. A flagship example is the Mesoamerican Biological Corridor (MBC), which aims to connect protected forest areas between Mexico and Panama to allow dispersal and gene flow of forest organisms. Because forests across Central America have continued to degrade, the functioning of the MBC has been questioned, but reliable estimates of species occurrence were unavailable. Large mammals are suitable indicators of forest functioning, so we assessed their conservation status across the Isthmus of Panama, the narrowest section of the MBC. We used large-scale camera-trap surveys and hierarchical multispecies occupancy models in a Bayesian framework to estimate the occupancy of 9 medium to large mammals and developed an occupancy-weighted connectivity metric to evaluate species-specific functional connectivity. White-lipped peccary (Tayassu pecari), jaguar (Panthera onca), giant anteater (Myrmecophaga tridactyla), white-tailed deer (Odocoileus virginianus), and tapir (Tapirus bairdii) had low expected occupancy along the MBC in Panama. Puma (Puma concolor), red brocket deer (Mazama temama), ocelot (Leopardus pardalis), and collared peccary (Pecari tajacu), which are more adaptable, had higher occupancy, even in areas with low forest cover near infrastructure. However, the majority of species were subject to ≥1 gap that was larger than their known dispersal distances, suggesting poor connectivity along the MBC in Panama. Based on our results, forests in Darien, Donoso–Santa Fe, and La Amistad International Park are critical for survival of large terrestrial mammals in Panama and 2 areas need restoration. |