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The scope and severity of white-nose syndrome on hibernating bats in North America.
Cheng, Tina L; Reichard, Jonathan D; Coleman, Jeremy T H; Weller, Theodore J; Thogmartin, Wayne E; Reichert, Brian E; Bennett, Alyssa B; Broders, Hugh G; Campbell, Joshua; Etchison, Katherine; Feller, Daniel J; Geboy, Richard; Hemberger, Traci; Herzog, Carl; Hicks, Alan C; Houghton, Sandra; Humber, Jessica; Kath, Joseph A; King, R Andrew; Loeb, Susan C; Massé, Ariane; Morris, Katrina M; Niederriter, Holly; Nordquist, Gerda; Perry, Roger W; Reynolds, Richard J; Sasse, D Blake; Scafini, Michael R; Stark, Richard C; Stihler, Craig W; Thomas, Steven C; Turner, Gregory G; Webb, Shevenell; Westrich, Bradford J; Frick, Winifred F.
Afiliação
  • Cheng TL; Bat Conservation International, 500 North Capital of Texas Highway, Building 1, Austin, TX, 78746, U.S.A.
  • Reichard JD; Ecological Services, U.S. Fish and Wildlife Service, 300 Westgate Center Drive, Hadley, MA, 01035, U.S.A.
  • Coleman JTH; Ecological Services, U.S. Fish and Wildlife Service, 300 Westgate Center Drive, Hadley, MA, 01035, U.S.A.
  • Weller TJ; Pacific Southwest Research Station, U.S. Department of Agriculture, 1700 Bayview Drive, Arcata, CA, 95521, U.S.A.
  • Thogmartin WE; Upper Midwest Environmental Sciences Center, U.S. Geological Survey, 2630 Fanta Reed Road, La Crosse, WI, 54601, U.S.A.
  • Reichert BE; Fort Collins Science Center, U.S. Geological Survey, 2150 Centre Avenue, Fort Collins, CO, 80526, U.S.A.
  • Bennett AB; Vermont Department of Fish and Wildlife, 111 West St., Essex Junction, VT, 05452, U.S.A.
  • Broders HG; Saint Mary's University, 923 Robie St., Halifax, NS, B3H 3C3, Canada.
  • Campbell J; Tennessee Wildlife Resources Agency, 5107 Edmonson Pike, Nashville, TN, 37211, U.S.A.
  • Etchison K; Mississippi Department of Wildlife, 1505 Eastover Dr., Jackson, MS, 39211, U.S.A.
  • Feller DJ; Maryland Department of Natural Resources, 580 Taylor Ave., Frostburg, MD, 21401, U.S.A.
  • Geboy R; U.S. Fish and Wildlife Service, 520 S. Walker St., Bloomington, IN, 47403, U.S.A.
  • Hemberger T; Kentucky Department of Fish and Wildlife Resources, 1 Sportsman's Ln., Frankfort, KY, 40601, U.S.A.
  • Herzog C; New York Department of Environmental Conservation, 625 Broadway, Albany, NY, 12233, U.S.A.
  • Hicks AC; New York Department of Environmental Conservation, 625 Broadway, Albany, NY, 12233, U.S.A.
  • Houghton S; New Hampshire Fish and Game, 11 Hazen Dr., Concord, NH, 03301, U.S.A.
  • Humber J; NL Wildlife Division, Government of Newfoundland and Labrador, 192 Wheeler's Rd., P.O. Box 2006, Corner Brook, NL, A2H 0J1, Canada.
  • Kath JA; Illinois Department of Natural Resources, 1 Natural Resources Way, Springfield, IL, 62702, U.S.A.
  • King RA; U.S. Fish and Wildlife Service, 520 S. Walker St., Bloomington, IN, 47403, U.S.A.
  • Loeb SC; Southern Research Station, U.S. Forest Service, Clemson University, 233 Lehotsky Hall, Clemson, SC, 29634, U.S.A.
  • Massé A; Ministère des Forêts, de la Faune et des Parcs, 880 ch. Sainte-Foy, Québec, QC, G1S 4X4, Canada.
  • Morris KM; Wildlife Conservation Section, Georgia Department of Natural Resources, 2065 US Hwy 278 SE, Social Circle, GA, 30025, U.S.A.
  • Niederriter H; Delaware Department of Natural Resources and Environmental Control, Richardson and Robbins Bldg., 89 Kings Hwy SW, Dover, DE, 19901, U.S.A.
  • Nordquist G; Minnesota Department of Natural Resources, 500 Lafayette Rd., Saint Paul, MN, 55155, U.S.A.
  • Perry RW; U.S. Forest Service, 100 Reserve St., Hot Springs, AR, 71901, U.S.A.
  • Reynolds RJ; Virginia Department of Wildlife Resources, 7870 Villa Park Dr. #400, Richmond, VA, 23228, U.S.A.
  • Sasse DB; Arkansas Game and Fish Commission, 2 Natural Resources Dr., Little Rock, AR, 72205, U.S.A.
  • Scafini MR; Pennsylvania Game Commission, 2001 Elmerton Ave., Harrisburg, PA, 17110, U.S.A.
  • Stark RC; U.S. Fish and Wildlife Service, 9014 E. 21st St., Tulsa, OK, 74129, U.S.A.
  • Stihler CW; West Virginia Division of Natural Resources, P.O. Box 67, Elkins, WV, 26241, U.S.A.
  • Thomas SC; National Park Service, Cumberland Piedmont Inventory and Monitoring Network, Mammoth Cave National Park, P.O. Box 8, Mammoth Cave, KY, 42259, U.S.A.
  • Turner GG; Pennsylvania Game Commission, 2001 Elmerton Ave., Harrisburg, PA, 17110, U.S.A.
  • Webb S; Maine Department of Inland Fisheries and Wildlife, 284 State St., Augusta, ME, 04330, U.S.A.
  • Westrich BJ; Indiana Department of Natural Resources, 402 W. Washington St., Indianapolis, IN, 46204, U.S.A.
  • Frick WF; Bat Conservation International, 500 North Capital of Texas Highway, Building 1, Austin, TX, 78746, U.S.A.
Conserv Biol ; 35(5): 1586-1597, 2021 10.
Article em En | MEDLINE | ID: mdl-33877716
ABSTRACT
Assessing the scope and severity of threats is necessary for evaluating impacts on populations to inform conservation planning. Quantitative threat assessment often requires monitoring programs that provide reliable data over relevant spatial and temporal scales, yet such programs can be difficult to justify until there is an apparent stressor. Leveraging efforts of wildlife management agencies to record winter counts of hibernating bats, we collated data for 5 species from over 200 sites across 27 U.S. states and 2 Canadian provinces from 1995 to 2018 to determine the impact of white-nose syndrome (WNS), a deadly disease of hibernating bats. We estimated declines of winter counts of bat colonies at sites where the invasive fungus that causes WNS (Pseudogymnoascus destructans) had been detected to assess the threat impact of WNS. Three species undergoing species status assessment by the U.S. Fish and Wildlife Service (Myotis septentrionalis, Myotis lucifugus, and Perimyotis subflavus) declined by more than 90%, which warrants classifying the severity of the WNS threat as extreme based on criteria used by NatureServe. The scope of the WNS threat as defined by NatureServe criteria was large (36% of Myotis lucifugus range) to pervasive (79% of Myotis septentrionalis range) for these species. Declines for 2 other species (Myotis sodalis and Eptesicus fuscus) were less severe but still qualified as moderate to serious based on NatureServe criteria. Data-sharing across jurisdictions provided a comprehensive evaluation of scope and severity of the threat of WNS and indicated regional differences that can inform response efforts at international, national, and state or provincial jurisdictions. We assessed the threat impact of an emerging infectious disease by uniting monitoring efforts across jurisdictional boundaries and demonstrated the importance of coordinated monitoring programs, such as the North American Bat Monitoring Program (NABat), for data-driven conservation assessments and planning.
RESUMEN
Alcance y Severidad del Síndrome de Nariz Blanca en los Murciélagos Hibernando en América del Norte Resumen La evaluación del alcance y la severidad de las amenazas es necesaria para los análisis de impacto sobre las poblaciones que se usan para orientar a la planeación de la conservación. La evaluación cuantitativa de amenazas con frecuencia requiere de programas de monitoreo que proporcionen datos confiables en escalas espaciales y temporales, aunque dichos programas pueden ser difíciles de justificar hasta que exista un estresante aparente. Gracias a una movilización de esfuerzos de las agencias de manejo de fauna para registrar los conteos invernales de murciélagos hibernadores, recopilamos datos para cinco especies en más de 200 sitios a lo largos de 27 estados de EUA y dos provincias canadienses entre 1995 y 2018 para determinar el impacto del síndrome de nariz blanca (SNB), una enfermedad mortal de los murciélagos hibernadores. Estimamos declinaciones en los conteos invernales de las colonias de murciélagos en sitios en donde el hongo invasivo que ocasiona el SNB (Pseudogymnoascus destructans) había sido detectado para evaluar el impacto de amenaza del SNB. Tres especies que se encuentran bajo valoración por parte del Servicio de Pesca y Vida Silvestre de los EUA (Myotis septentrionalis, Myotis lucifugus y Perimyotis subflavus) tuvieron una declinación de más del 90%, lo que justifica la clasificación de la severidad de la amenaza del SNB como extrema con base en el criterio usado por NatureServe. El alcance de la amenaza del SNB definido por el criterio de NatureServe fue desde amplio (36% de la distribución de Myotis lucifugus) hasta dominante (79% de la distribución de Myotis septentrionalis) para estas especies. Las declinaciones de otras dos especies (Myotis sodalis y Eptesicus fuscus) fueron menos severas, pero de igual manera quedaron clasificadas desde moderada hasta seria con base en los criterios de NatureServe. El intercambio de datos entre las jurisdicciones proporcionó una evaluación completa del alcance y la severidad de la amenaza del SNB e indicó las diferencias regionales que pueden guiar a los esfuerzos de respuesta realizados en las jurisdicciones internacionales, nacionales, estatales o provinciales. Evaluamos el impacto de amenaza de una enfermedad infecciosa emergente mediante la combinación de los esfuerzos de monitoreo que sobrepasan fronteras jurisdiccionales y demostramos la importancia que tienen para la planeación y la evaluación basadas en datos de la conservación los programas de monitoreo coordinados, como el Programa de Monitoreo de los Murciélagos Norteamericanos (NABat).
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Texto completo: 1 Coleções: 01-internacional Base de dados: MEDLINE Assunto principal: Quirópteros / Hibernação Limite: Animals País/Região como assunto: America do norte Idioma: En Ano de publicação: 2021 Tipo de documento: Article

Texto completo: 1 Coleções: 01-internacional Base de dados: MEDLINE Assunto principal: Quirópteros / Hibernação Limite: Animals País/Região como assunto: America do norte Idioma: En Ano de publicação: 2021 Tipo de documento: Article