Wind Energy Development: Methods to Assess Bird and Bat Fatality Rates Post-Construction
Monitoring fatalities at wind energy facilities after they have been constructed can provide valuable information regarding impacts of wind power development on wildlife. The objective of this monitoring is to estimate abundance of a super-population of carcasses that entered the area within a desig...
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doaj-56a6a04729a44a1f9c0f65cffcaf353d2020-11-25T03:25:46ZengUtah State UniversityHuman-Wildlife Interactions2155-38742155-38742017-02-0110110.26077/36fe-0296Wind Energy Development: Methods to Assess Bird and Bat Fatality Rates Post-ConstructionManuela Huso0Dan Dalthorp1T. J. Miller2Dawn Bruns3U.S. Geological SurveyU.S. Geological SurveyU.S. Fish and Wildlife ServiceU.S. Fish and Wildlife ServiceMonitoring fatalities at wind energy facilities after they have been constructed can provide valuable information regarding impacts of wind power development on wildlife. The objective of this monitoring is to estimate abundance of a super-population of carcasses that entered the area within a designated period of time. By definition, the population is not closed and carcasses can enter as they are killed through collision with turbines, and leave as they are removed by scavengers or decompose to a point where they are not recognizable. In addition, the population is not inherently mobile, but can only change location through some external force. A focus on number of animal carcasses comprising the super-population, combined with peculiar traits that resist classic assumptions, distinguish fatality estimation at wind-power facilities from more classic abundance estimates that can be addressed through mark-recapture techniques or other well-known abundance estimators. We review the available methods to estimate the super-population of carcasses at wind power facilities. We discuss the role of these estimates in determining appropriate levels of minimization and mitigation of impacts to individual species of concern. We discuss the potential to extrapolate these measurements to reflect the cumulative effect of the industry on individual species. Finally, we suggest avenues of research needed to strengthen our understanding of the effect wind power development has, and might have in the future, on wildlife on this continent and worldwide. https://digitalcommons.usu.edu/hwi/vol10/iss1/8bayes’ theoremcredible intervalsdetection probabilityfatality estimator |
collection |
DOAJ |
language |
English |
format |
Article |
sources |
DOAJ |
author |
Manuela Huso Dan Dalthorp T. J. Miller Dawn Bruns |
spellingShingle |
Manuela Huso Dan Dalthorp T. J. Miller Dawn Bruns Wind Energy Development: Methods to Assess Bird and Bat Fatality Rates Post-Construction Human-Wildlife Interactions bayes’ theorem credible intervals detection probability fatality estimator |
author_facet |
Manuela Huso Dan Dalthorp T. J. Miller Dawn Bruns |
author_sort |
Manuela Huso |
title |
Wind Energy Development: Methods to Assess Bird and Bat Fatality Rates Post-Construction |
title_short |
Wind Energy Development: Methods to Assess Bird and Bat Fatality Rates Post-Construction |
title_full |
Wind Energy Development: Methods to Assess Bird and Bat Fatality Rates Post-Construction |
title_fullStr |
Wind Energy Development: Methods to Assess Bird and Bat Fatality Rates Post-Construction |
title_full_unstemmed |
Wind Energy Development: Methods to Assess Bird and Bat Fatality Rates Post-Construction |
title_sort |
wind energy development: methods to assess bird and bat fatality rates post-construction |
publisher |
Utah State University |
series |
Human-Wildlife Interactions |
issn |
2155-3874 2155-3874 |
publishDate |
2017-02-01 |
description |
Monitoring fatalities at wind energy facilities after they have been constructed can provide valuable information regarding impacts of wind power development on wildlife. The objective of this monitoring is to estimate abundance of a super-population of carcasses that entered the area within a designated period of time. By definition, the population is not closed and carcasses can enter as they are killed through collision with turbines, and leave as they are removed by scavengers or decompose to a point where they are not recognizable. In addition, the population is not inherently mobile, but can only change location through some external force. A focus on number of animal carcasses comprising the super-population, combined with peculiar traits that resist classic assumptions, distinguish fatality estimation at wind-power facilities from more classic abundance estimates that can be addressed through mark-recapture techniques or other well-known abundance estimators. We review the available methods to estimate the super-population of carcasses at wind power facilities. We discuss the role of these estimates in determining appropriate levels of minimization and mitigation of impacts to individual species of concern. We discuss the potential to extrapolate these measurements to reflect the cumulative effect of the industry on individual species. Finally, we suggest avenues of research needed to strengthen our understanding of the effect wind power development has, and might have in the future, on wildlife on this continent and worldwide.
|
topic |
bayes’ theorem credible intervals detection probability fatality estimator |
url |
https://digitalcommons.usu.edu/hwi/vol10/iss1/8 |
work_keys_str_mv |
AT manuelahuso windenergydevelopmentmethodstoassessbirdandbatfatalityratespostconstruction AT dandalthorp windenergydevelopmentmethodstoassessbirdandbatfatalityratespostconstruction AT tjmiller windenergydevelopmentmethodstoassessbirdandbatfatalityratespostconstruction AT dawnbruns windenergydevelopmentmethodstoassessbirdandbatfatalityratespostconstruction |
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