• 文献检索
  • 文档翻译
  • 深度研究
  • 学术资讯
  • Suppr Zotero 插件Zotero 插件
  • 邀请有礼
  • 套餐&价格
  • 历史记录
应用&插件
Suppr Zotero 插件Zotero 插件浏览器插件Mac 客户端Windows 客户端微信小程序
定价
高级版会员购买积分包购买API积分包
服务
文献检索文档翻译深度研究API 文档MCP 服务
关于我们
关于 Suppr公司介绍联系我们用户协议隐私条款
关注我们

Suppr 超能文献

核心技术专利:CN118964589B侵权必究
粤ICP备2023148730 号-1Suppr @ 2026

文献检索

告别复杂PubMed语法,用中文像聊天一样搜索,搜遍4000万医学文献。AI智能推荐,让科研检索更轻松。

立即免费搜索

文件翻译

保留排版,准确专业,支持PDF/Word/PPT等文件格式,支持 12+语言互译。

免费翻译文档

深度研究

AI帮你快速写综述,25分钟生成高质量综述,智能提取关键信息,辅助科研写作。

立即免费体验

欧洲淡水生物多样性的恢复已陷入停滞。

The recovery of European freshwater biodiversity has come to a halt.

机构信息

Department of River Ecology and Conservation, Senckenberg Research Institute and Natural History Museum Frankfurt, Gelnhausen, Germany.

Faculty of Biology, University of Duisburg-Essen, Essen, Germany.

出版信息

Nature. 2023 Aug;620(7974):582-588. doi: 10.1038/s41586-023-06400-1. Epub 2023 Aug 9.

DOI:10.1038/s41586-023-06400-1
PMID:37558875
原文链接:https://pmc.ncbi.nlm.nih.gov/articles/PMC10432276/
Abstract

Owing to a long history of anthropogenic pressures, freshwater ecosystems are among the most vulnerable to biodiversity loss. Mitigation measures, including wastewater treatment and hydromorphological restoration, have aimed to improve environmental quality and foster the recovery of freshwater biodiversity. Here, using 1,816 time series of freshwater invertebrate communities collected across 22 European countries between 1968 and 2020, we quantified temporal trends in taxonomic and functional diversity and their responses to environmental pressures and gradients. We observed overall increases in taxon richness (0.73% per year), functional richness (2.4% per year) and abundance (1.17% per year). However, these increases primarily occurred before the 2010s, and have since plateaued. Freshwater communities downstream of dams, urban areas and cropland were less likely to experience recovery. Communities at sites with faster rates of warming had fewer gains in taxon richness, functional richness and abundance. Although biodiversity gains in the 1990s and 2000s probably reflect the effectiveness of water-quality improvements and restoration projects, the decelerating trajectory in the 2010s suggests that the current measures offer diminishing returns. Given new and persistent pressures on freshwater ecosystems, including emerging pollutants, climate change and the spread of invasive species, we call for additional mitigation to revive the recovery of freshwater biodiversity.

摘要

由于长期受到人为压力的影响,淡水生态系统是最容易受到生物多样性丧失影响的生态系统之一。减轻这些压力的措施,包括污水处理和水力学形态恢复,旨在改善环境质量,促进淡水生物多样性的恢复。在这里,我们使用了 1968 年至 2020 年间在 22 个欧洲国家收集的 1816 个淡水无脊椎动物群落的时间序列数据,量化了分类和功能多样性的时间趋势及其对环境压力和梯度的响应。我们观察到分类 richness(每年增加 0.73%)、功能 richness(每年增加 2.4%)和丰度(每年增加 1.17%)的总体增加。然而,这些增加主要发生在 21 世纪 10 年代之前,此后已经趋于平稳。大坝下游、城市地区和农田的淡水群落不太可能经历恢复。在变暖速度较快的地点,群落的分类 richness、功能 richness 和丰度增益较少。尽管 20 世纪 90 年代和 21 世纪初的生物多样性增长可能反映了水质改善和恢复项目的有效性,但 21 世纪 10 年代以来的减速轨迹表明,目前的措施带来的回报越来越少。鉴于淡水生态系统面临新的和持续的压力,包括新兴污染物、气候变化和入侵物种的传播,我们呼吁采取额外的缓解措施,以恢复淡水生物多样性的恢复。

https://cdn.ncbi.nlm.nih.gov/pmc/blobs/58e4/10432276/bc03b2463789/41586_2023_6400_Fig14_ESM.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/58e4/10432276/7e0e60464f75/41586_2023_6400_Fig1_HTML.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/58e4/10432276/8514de04cfba/41586_2023_6400_Fig2_HTML.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/58e4/10432276/51daed149a63/41586_2023_6400_Fig3_HTML.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/58e4/10432276/f9c4dbd09467/41586_2023_6400_Fig4_HTML.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/58e4/10432276/9de117232bde/41586_2023_6400_Fig5_ESM.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/58e4/10432276/7eeb2c516933/41586_2023_6400_Fig6_ESM.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/58e4/10432276/dee1eabbcf8e/41586_2023_6400_Fig7_ESM.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/58e4/10432276/81f91ce356f4/41586_2023_6400_Fig8_ESM.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/58e4/10432276/eadbc38f28f8/41586_2023_6400_Fig9_ESM.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/58e4/10432276/bb2b86bff52a/41586_2023_6400_Fig10_ESM.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/58e4/10432276/9c83db6b90cf/41586_2023_6400_Fig11_ESM.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/58e4/10432276/d39b0c3c47c5/41586_2023_6400_Fig12_ESM.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/58e4/10432276/4c913345fc6f/41586_2023_6400_Fig13_ESM.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/58e4/10432276/bc03b2463789/41586_2023_6400_Fig14_ESM.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/58e4/10432276/7e0e60464f75/41586_2023_6400_Fig1_HTML.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/58e4/10432276/8514de04cfba/41586_2023_6400_Fig2_HTML.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/58e4/10432276/51daed149a63/41586_2023_6400_Fig3_HTML.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/58e4/10432276/f9c4dbd09467/41586_2023_6400_Fig4_HTML.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/58e4/10432276/9de117232bde/41586_2023_6400_Fig5_ESM.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/58e4/10432276/7eeb2c516933/41586_2023_6400_Fig6_ESM.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/58e4/10432276/dee1eabbcf8e/41586_2023_6400_Fig7_ESM.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/58e4/10432276/81f91ce356f4/41586_2023_6400_Fig8_ESM.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/58e4/10432276/eadbc38f28f8/41586_2023_6400_Fig9_ESM.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/58e4/10432276/bb2b86bff52a/41586_2023_6400_Fig10_ESM.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/58e4/10432276/9c83db6b90cf/41586_2023_6400_Fig11_ESM.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/58e4/10432276/d39b0c3c47c5/41586_2023_6400_Fig12_ESM.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/58e4/10432276/4c913345fc6f/41586_2023_6400_Fig13_ESM.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/58e4/10432276/bc03b2463789/41586_2023_6400_Fig14_ESM.jpg

相似文献

1
The recovery of European freshwater biodiversity has come to a halt.欧洲淡水生物多样性的恢复已陷入停滞。
Nature. 2023 Aug;620(7974):582-588. doi: 10.1038/s41586-023-06400-1. Epub 2023 Aug 9.
2
Multi-decadal improvements in the ecological quality of European rivers are not consistently reflected in biodiversity metrics.多十年以来,欧洲河流的生态质量得到了改善,但这并没有在生物多样性指标上得到一致反映。
Nat Ecol Evol. 2024 Mar;8(3):430-441. doi: 10.1038/s41559-023-02305-4. Epub 2024 Jan 26.
3
Hydromorphological degradation modifies long-term macroinvertebrate responses to water quality and climate changes in lowland rivers.水形态学退化改变了低地河流中长期大型无脊椎动物对水质和气候变化的响应。
Environ Res. 2024 Nov 15;261:119638. doi: 10.1016/j.envres.2024.119638. Epub 2024 Jul 18.
4
Mitigation of urbanization effects on aquatic ecosystems by synchronous ecological restoration.通过同步生态恢复减轻城市化对水生态系统的影响。
Water Res. 2021 Oct 1;204:117587. doi: 10.1016/j.watres.2021.117587. Epub 2021 Aug 21.
5
Significant improvement in freshwater invertebrate biodiversity in all types of English rivers over the past 30 years.在过去30年里,英国各类河流中的淡水无脊椎动物生物多样性有了显著改善。
Sci Total Environ. 2023 Dec 20;905:167144. doi: 10.1016/j.scitotenv.2023.167144. Epub 2023 Sep 18.
6
Divergent temporal responses of native macroinvertebrate communities to biological invasions.本地大型无脊椎动物群落对生物入侵的时滞反应存在差异。
Glob Chang Biol. 2024 Oct;30(10):e17521. doi: 10.1111/gcb.17521.
7
Structural and functional responses of invertebrate communities to climate change and flow regulation in alpine catchments.高寒流域气候变化和水流调控对无脊椎动物群落结构和功能的响应
Glob Chang Biol. 2019 May;25(5):1612-1628. doi: 10.1111/gcb.14581. Epub 2019 Mar 3.
8
Neonicotinoids and fertilizers jointly structure naturally assembled freshwater macroinvertebrate communities.新烟碱类杀虫剂和肥料共同构建了自然组装的淡水大型无脊椎动物群落。
Sci Total Environ. 2019 Nov 15;691:36-44. doi: 10.1016/j.scitotenv.2019.07.110. Epub 2019 Jul 8.
9
Long-term trends and drivers of biological invasion in Central European streams.中欧河流生物入侵的长期趋势及驱动因素
Sci Total Environ. 2023 Jun 10;876:162817. doi: 10.1016/j.scitotenv.2023.162817. Epub 2023 Mar 15.
10
Species specific responses to stressors hamper Trichoptera recovery.物种对胁迫的特异性反应阻碍了蜉蝣的恢复。
Sci Total Environ. 2024 Oct 1;945:173992. doi: 10.1016/j.scitotenv.2024.173992. Epub 2024 Jun 18.

引用本文的文献

1
Different Mechanisms Explain Decoupled Co-Occurrence Patterns of Native and Non-Native Macroinvertebrates.不同机制解释了本地和非本地大型无脊椎动物解耦共生模式。
Glob Chang Biol. 2025 Aug;31(8):e70417. doi: 10.1111/gcb.70417.
2
Unravelling the long-term river health status of Kruger National Park Rivers using macroinvertebrate-based monitoring.利用基于大型无脊椎动物的监测揭示克鲁格国家公园河流的长期健康状况。
Environ Monit Assess. 2025 Jul 14;197(8):914. doi: 10.1007/s10661-025-14343-5.
3
Standardized diversity estimation uncovers global distribution patterns and drivers of stream insects.

本文引用的文献

1
From meta-system theory to the sustainable management of rivers in the Anthropocene.从元系统理论到人类世河流的可持续管理
Front Ecol Environ. 2022 Feb;20(1):49-57. doi: 10.1002/fee.2417. Epub 2021 Oct 5.
2
Characterising functional strategies and trait space of freshwater macroinvertebrates.描述淡水大型无脊椎动物的功能策略和特征空间。
Sci Rep. 2022 Jul 19;12(1):12283. doi: 10.1038/s41598-022-16472-0.
3
Is water quality in British rivers "better than at any time since the end of the Industrial Revolution"?英国河流的水质是否“优于工业革命结束以来的任何时候”?
标准化多样性估计揭示了溪流昆虫的全球分布模式及其驱动因素。
NPJ Biodivers. 2025 Jul 3;4(1):27. doi: 10.1038/s44185-025-00098-2.
4
Global elevation of algal bloom frequency in large lakes over the past two decades.过去二十年大湖中藻华频率的全球升高。
Natl Sci Rev. 2025 Jan 11;12(3):nwaf011. doi: 10.1093/nsr/nwaf011. eCollection 2025 Mar.
5
Global Patterns and Drivers of Freshwater Fish Extinctions: Can We Learn From Our Losses?淡水鱼灭绝的全球模式与驱动因素:我们能从损失中吸取教训吗?
Glob Chang Biol. 2025 May;31(5):e70244. doi: 10.1111/gcb.70244.
6
Analysing factors underlying the reporting of established non-native species.分析已确定的非本地物种报告背后的因素。
Sci Rep. 2025 Apr 10;15(1):12337. doi: 10.1038/s41598-025-96133-0.
7
A summer in the greater Paris: trophic status of peri-urban lakes shapes prokaryotic community structure and functional potential.大巴黎地区的一个夏天:城郊湖泊的营养状况塑造了原核生物群落结构和功能潜力。
Environ Microbiome. 2025 Feb 17;20(1):24. doi: 10.1186/s40793-025-00681-x.
8
Zinc and Copper Have the Greatest Relative Importance for River Macroinvertebrate Richness at a National Scale.在国家尺度上,锌和铜对河流大型无脊椎动物丰富度具有最大的相对重要性。
Environ Sci Technol. 2025 Mar 4;59(8):4068-4079. doi: 10.1021/acs.est.4c06849. Epub 2025 Feb 17.
9
Usual suspects meet mission impossible: Nutrient losses and effects of mitigation measures on a coastal catchment in the Baltic Sea region.常见因素遭遇不可能完成的任务:波罗的海地区一个沿海集水区的养分流失及缓解措施的影响。
Ambio. 2025 Jun;54(6):1026-1042. doi: 10.1007/s13280-025-02132-w. Epub 2025 Feb 3.
10
Recovery and Degradation Drive Changes in the Dispersal Capacity of Stream Macroinvertebrate Communities.恢复与退化驱动溪流大型无脊椎动物群落扩散能力的变化。
Glob Chang Biol. 2025 Jan;31(1):e70054. doi: 10.1111/gcb.70054.
Sci Total Environ. 2022 Oct 15;843:157014. doi: 10.1016/j.scitotenv.2022.157014. Epub 2022 Jun 27.
4
Multidecadal changes in functional diversity lag behind the recovery of taxonomic diversity.功能多样性的数十年变化滞后于分类多样性的恢复。
Ecol Evol. 2021 Nov 23;11(23):17471-17484. doi: 10.1002/ece3.8381. eCollection 2021 Dec.
5
A global agenda for advancing freshwater biodiversity research.推进淡水生物多样性研究的全球议程。
Ecol Lett. 2022 Feb;25(2):255-263. doi: 10.1111/ele.13931. Epub 2021 Dec 1.
6
Common irrigation drivers of freshwater salinisation in river basins worldwide.全球流域淡水盐化的常见灌溉驱动因素。
Nat Commun. 2021 Jul 9;12(1):4232. doi: 10.1038/s41467-021-24281-8.
7
Pervasive decline of subtropical aquatic insects over 20 years driven by water transparency, non-native fish and stoichiometric imbalance.20 年来,由于水透明度、非本地鱼类和化学计量失衡,亚热带水生昆虫普遍减少。
Biol Lett. 2021 Jun;17(6):20210137. doi: 10.1098/rsbl.2021.0137. Epub 2021 Jun 9.
8
The dimensionality and structure of species trait spaces.物种特征空间的维度和结构。
Ecol Lett. 2021 Sep;24(9):1988-2009. doi: 10.1111/ele.13778. Epub 2021 May 20.
9
How long do population level field experiments need to be? Utilising data from the 40-year-old LTER network.人口水平的野外实验需要进行多长时间?利用来自已有 40 年历史的 LTER 网络的数据。
Ecol Lett. 2021 May;24(5):1103-1111. doi: 10.1111/ele.13710. Epub 2021 Feb 22.
10
Multiple stressors determine river ecological status at the European scale: Towards an integrated understanding of river status deterioration.多种胁迫因素决定了欧洲河流的生态状况:对河流状况恶化的综合理解。
Glob Chang Biol. 2021 May;27(9):1962-1975. doi: 10.1111/gcb.15504. Epub 2021 Feb 19.