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231225s2021 xx |||||o 00| ||eng c |
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|a 10.1111/cobi.13457
|2 doi
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|a pubmed24n1017.xml
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|a (NLM)31913528
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|a DE-627
|b ger
|c DE-627
|e rakwb
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|a eng
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|a Conkling, Tara J
|e verfasserin
|4 aut
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|a Limitations, lack of standardization, and recommended best practices in studies of renewable energy effects on birds and bats
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|c 2021
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|a Text
|b txt
|2 rdacontent
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|a ƒaComputermedien
|b c
|2 rdamedia
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|a ƒa Online-Ressource
|b cr
|2 rdacarrier
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|a Date Completed 26.04.2021
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|a Date Revised 26.04.2021
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|a published: Print-Electronic
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|a Citation Status MEDLINE
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|a © 2020 Society for Conservation Biology.
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|a Increasing global energy demand is fostering the development of renewable energy as an alternative to fossil fuels. However, renewable energy facilities may adversely affect wildlife. Facility siting guidelines recommend or require project developers complete pre- and postconstruction wildlife surveys to predict risk and estimate effects of proposed projects. Despite this, there are no published studies that have quantified the types of surveys used or how survey types are standardized within and across facilities. We evaluated 628 peer-reviewed publications, unpublished reports, and citations, and we analyzed data from 525 of these sources (203 facilities: 193 wind and 10 solar) in the United States and Canada to determine the frequency of pre- and postconstruction surveys and whether that frequency changed over time; frequency of studies explicitly designed to allow before-after or impact-control analyses; and what types of survey data were collected during pre- and postconstruction periods and how those data types were standardized across periods and among facilities. Within our data set, postconstruction monitoring for wildlife fatalities and habitat use was a standard practice (n = 446 reports), but preconstruction estimation of baseline wildlife habitat use and mortality was less frequently reported (n = 84). Only 22% (n = 45) of the 203 facilities provided data from both pre- and postconstruction, and 29% (n = 59) had experimental study designs. Of 108 facilities at which habitat-use surveys were conducted, only 3% estimated of detection probability. Thus, the available data generally preclude comparison of biological data across construction periods and among facilities. Use of experimental study designs and following similar field protocols would improve the knowledge of how renewable energy affects wildlife. Article Impact Statement Many surveys at wind and solar facilities provide limited information on wildlife use and fatality rates
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|a Journal Article
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|a Research Support, Non-U.S. Gov't
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|a Research Support, U.S. Gov't, Non-P.H.S.
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|a Review
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|a best practices
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|a diseño experimental
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|a energía eólica
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|a energía renovable
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|a energía solar
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650 |
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|a experimental design
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|a mejores prácticas
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|a monitoreo de fauna
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650 |
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|a mortalidad
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|a mortality
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650 |
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|a renewable energy
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|a sampling bias
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|a sesgo de muestreo
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650 |
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|a solar energy
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650 |
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4 |
|a wildlife monitoring
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650 |
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4 |
|a wind energy
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650 |
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|a 可再生能源
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|a 太阳能
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|a 实验设计
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|a 最佳实践
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|a 死亡率
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|a 采样偏差
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650 |
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|a 野生动物监测
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650 |
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|a 风能
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700 |
1 |
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|a Loss, Scott R
|e verfasserin
|4 aut
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700 |
1 |
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|a Diffendorfer, Jay E
|e verfasserin
|4 aut
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1 |
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|a Duerr, Adam E
|e verfasserin
|4 aut
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1 |
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|a Katzner, Todd E
|e verfasserin
|4 aut
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773 |
0 |
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|i Enthalten in
|t Conservation biology : the journal of the Society for Conservation Biology
|d 1999
|g 35(2021), 1 vom: 15. Feb., Seite 64-76
|w (DE-627)NLM098176803
|x 1523-1739
|7 nnns
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|g volume:35
|g year:2021
|g number:1
|g day:15
|g month:02
|g pages:64-76
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|u http://dx.doi.org/10.1111/cobi.13457
|3 Volltext
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|a AR
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|d 35
|j 2021
|e 1
|b 15
|c 02
|h 64-76
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