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• W2022271276 abstract "Data collected by the Gap Analysis Program in the state of Idaho (U.S.A.) are used to prioritize the selection of locations for conservation action and research. Set coverage and integer programming algorithms provide a sequence of localities that maximize the number of species or vegetation classes represented at each step. Richness maps of vegetation cover class diversity, terrestrial vertebrate species diversity (“hot spot analysis”), endangered, threatened, and candidate species diversity, and unprotected vertebrate species diversity (“gap analysis”), when prioritized, show a rapid accumulation of species as more localities are chosen for terrestrial vertebrates and unprotected vertebrates. Gap analysis identifies four target areas (“gaps”) that include 79 of the 83 vertebrate species not currently protected. Accumulation of vegetation cover classes and endangered, threatened, and candidate species is much slower. Sweep analysis is used to determine how well prioritizing on one component of diversity accumulates other components. Endangered, threatened, and candidate species do not sweep total vertebrates as well as unprotected vertebrates do, but are better than vegetation classes. Total vertebrates sweep endangered, threatened, and candidate species better than unprotected vertebrates do, which in turn are better than vegetation classes. We emphasize that prioritization must be part of conservation efforts at multiple scales and that prioritization points out important localities where more detailed work mast be undertaken. Se utilizan datos obtenidos en el estado de Idaho (EUA) con el Gap Analysis Program (GAP) para priorizar la selección de localidades para acciones e investigación de conservación. La cobertura del conjunto y algoritmos de programación integral proporcionan una secuencia de localidades que maximizan el número de especies o tipos de vegetación representados en cada etapa. Los mapas de riqueza vegetal comprenden diversidad de tipos; diversidad de especies de vertebrados especies (“análisis de sitios álgidos”); diversidad de especies en peligro, amenazadas y candidatas, así como diversidad de especies no protegidas de vertebrados (“análisis de intervalos”). Al priorizarlos se muestra una rápida acumulación de especies a medida que seleccionan más localidades para vertebrados terrestres y vertebrados no protegidos. El análisis de intervalos identifica cuatro áreas (“intervalos”) que incluyen 79 de las 83 especies de vertebrados sin protección actualmente. La acumulación de tipos de vegetación, así como de especies en peligro, amenazadas y candidatas, es mucho más lenta. Se utiliza análisis de barrido para determinar la eficiencia de la acumulación de otros componentes al priorizar con uno de los componentes de la diversidad. Las especies en peligro, amenazadas y candidatas no barren al total de vertebrados con la eficiencia de las especies no protegidas, pero son mayores que los tipos de vegetación. El total de vertebrados barre mejor alas especies en peligro, amenazadas y candidatas que a los vertebrados no protegidos, los cuales a su vez son mejores que los tipos de vegetación. Enfatizamos que la priorización debe formar parte de los esfuerzos a escala múltiple y que la priorización identifica localidades importantes en las que se debe realizar trabajo mas detallado." @default.
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• W2022271276 date "1996-10-01" @default.
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• W2022271276 title "Conservation Prioritization Using GAP Data" @default.
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• W2022271276 doi "https://doi.org/10.1046/j.1523-1739.1996.10051332.x" @default.
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