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20231225134915.0 |
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231225s2020 xx |||||o 00| ||eng c |
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|a 10.1111/cobi.13490
|2 doi
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|a pubmed24n1032.xml
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|a (DE-627)NLM309893844
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|a (NLM)32406533
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|a DE-627
|b ger
|c DE-627
|e rakwb
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| 041 |
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|a eng
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| 100 |
1 |
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|a Rees, Matthew W
|e verfasserin
|4 aut
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| 245 |
1 |
0 |
|a Rapidly assessing cobenefits to advance threat-management alliances
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| 264 |
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1 |
|c 2020
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| 336 |
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|a Text
|b txt
|2 rdacontent
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| 337 |
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|a ƒaComputermedien
|b c
|2 rdamedia
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| 338 |
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|a ƒa Online-Ressource
|b cr
|2 rdacarrier
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| 500 |
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|a Date Completed 26.10.2020
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|a Date Revised 26.10.2020
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|a published: Print-Electronic
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|a Citation Status MEDLINE
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| 520 |
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|a © 2020 Society for Conservation Biology.
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|a Conservation strategies aimed at reducing threats to biodiversity can have significant implications for multiple sectors in a socioeconomic system, but these cobenefits are often poorly understood. For example, many of the threats to native species also impede agricultural production, yet agriculture is typically perceived as in competition with conservation objectives. Although a comprehensive, multiobjective decision analysis is usually beyond the scope and capacity of conservation decision makers, failing to incorporate key socioeconomic costs and benefits into conservation decision-making processes can result in missed opportunities for diversifying outcomes and creating cost-sharing multisectoral partnerships. We devised a straightforward and readily interpretable approach to incorporate cobenefits into a threat-management prioritization approach. We used it to analyze the agricultural cobenefits of implementing 9 invasive animal management strategies designed to ensure the persistence of 148 threatened species across Australia's Lake Eyre Basin over 50 years. A structured elicitation process with 24 participants (scientists, land managers, agriculturalists, and other stakeholders) was used to collect information on each strategy, including costs, technical and social feasibility, benefits to native threatened species, and cobenefits to agricultural production systems. The costs of targeted invasive animal management to save threatened species across the basin (AU$33 million/year) outweighed the overall benefits to the agricultural industry (estimated AU$226 million/year). The return on investment for these management strategies varied substantially when agricultural cobenefits were considered alongside threatened species benefits and showed synergies and challenges. Our approach demonstrates the value of incorporating cobenefits of conservation actions into cost-effectiveness analyses to guide potential investment and partnerships and to diversify implementation pathways
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4 |
|a Journal Article
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| 650 |
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4 |
|a Research Support, Non-U.S. Gov't
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| 650 |
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4 |
|a 保护的共同利益
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| 650 |
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4 |
|a Lake Eyre Basin
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| 650 |
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4 |
|a análisis de rentabilidad
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| 650 |
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4 |
|a cobeneficios de la conservación
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| 650 |
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4 |
|a conservation cobenefits
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| 650 |
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4 |
|a cost-effectiveness analysis
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| 650 |
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4 |
|a cuenca del Lago Eyre
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| 650 |
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4 |
|a decision support
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| 650 |
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4 |
|a economía ambiental
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| 650 |
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4 |
|a environmental economics
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| 650 |
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4 |
|a especie invasora
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| 650 |
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4 |
|a invasive species
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| 650 |
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4 |
|a investigación participativa
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| 650 |
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4 |
|a multiobjective decision making
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| 650 |
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4 |
|a participatory research
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| 650 |
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4 |
|a respaldo a las decisiones
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| 650 |
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4 |
|a toma de decisiones con objetivos múltiples
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| 650 |
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4 |
|a 入侵物种
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| 650 |
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4 |
|a 决策支持
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| 650 |
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4 |
|a 参与性研究
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| 650 |
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4 |
|a 多目标决策
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| 650 |
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4 |
|a 成本效益分析
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| 650 |
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4 |
|a 环境经济学
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| 650 |
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4 |
|a 艾尔湖盆地
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| 700 |
1 |
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|a Carwardine, Josie
|e verfasserin
|4 aut
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| 700 |
1 |
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|a Reeson, Andrew
|e verfasserin
|4 aut
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| 700 |
1 |
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|a Firn, Jennifer
|e verfasserin
|4 aut
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| 773 |
0 |
8 |
|i Enthalten in
|t Conservation biology : the journal of the Society for Conservation Biology
|d 1999
|g 34(2020), 4 vom: 01. Aug., Seite 843-853
|w (DE-627)NLM098176803
|x 1523-1739
|7 nnns
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| 773 |
1 |
8 |
|g volume:34
|g year:2020
|g number:4
|g day:01
|g month:08
|g pages:843-853
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| 856 |
4 |
0 |
|u http://dx.doi.org/10.1111/cobi.13490
|3 Volltext
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|d 34
|j 2020
|e 4
|b 01
|c 08
|h 843-853
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