濒危物种
IUCN红色名录
生物多样性
生态学
淡水生态系统
消光(光学矿物学)
濒危物种
近危物种
物种丰富度
过度开采
非生物成分
地理
栖息地
生物
生态系统
古生物学
作者
Catherine Overed-Sayer,Eresha Fernando,Randall R. Jiménez,Nicholas B. W. Macfarlane,Giovanni Rapacciuolo,Monika Böhm,Thomas M. Brooks,Topiltzin Contreras‐MacBeath,Neil A. Cox,Ian Harrison,Michael Hoffmann,Richard K. B. Jenkins,Kevin G. Smith,Jean-Christophe Vié,John C. Abbott,David J. Allen,Gerald R. Allen,Violeta Barrios,Jean‐Pierre Boudot,Savrina F. Carrizo
出处
期刊:Nature
[Nature Portfolio]
日期:2025-01-08
被引量:28
标识
DOI:10.1038/s41586-024-08375-z
摘要
Abstract Freshwater ecosystems are highly biodiverse 1 and important for livelihoods and economic development 2 , but are under substantial stress 3 . To date, comprehensive global assessments of extinction risk have not included any speciose groups primarily living in freshwaters. Consequently, data from predominantly terrestrial tetrapods 4,5 are used to guide environmental policy 6 and conservation prioritization 7 , whereas recent proposals for target setting in freshwaters use abiotic factors 8–13 . However, there is evidence 14–17 that such data are insufficient to represent the needs of freshwater species and achieve biodiversity goals 18,19 . Here we present the results of a multi-taxon global freshwater fauna assessment for The IUCN Red List of Threatened Species covering 23,496 decapod crustaceans, fishes and odonates, finding that one-quarter are threatened with extinction. Prevalent threats include pollution, dams and water extraction, agriculture and invasive species, with overharvesting also driving extinctions. We also examined the degree of surrogacy of both threatened tetrapods and freshwater abiotic factors (water stress and nitrogen) for threatened freshwater species. Threatened tetrapods are good surrogates when prioritizing sites to maximize rarity-weighted richness, but poorer when prioritizing based on the most range-restricted species. However, they are much better surrogates than abiotic factors, which perform worse than random. Thus, although global priority regions identified for tetrapod conservation are broadly reflective of those for freshwater faunas, given differences in key threats and habitats, meeting the needs of tetrapods cannot be assumed sufficient to conserve freshwater species at local scales.
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