4.8 Article

Multiple stressors determine river ecological status at the European scale: Towards an integrated understanding of river status deterioration

期刊

GLOBAL CHANGE BIOLOGY
卷 27, 期 9, 页码 1962-1975

出版社

WILEY
DOI: 10.1111/gcb.15504

关键词

ecological status; hydrology; nutrients; riparian land use; river types; stressor interactions; toxic substances

资金

  1. European research projects MARS (Managing Aquatic ecosystems and water Resources)
  2. SOLUTIONS (Solutions for present and future emerging pollutants in land and water resources management) - European Union [603378, 603437]
  3. Dutch program `Water Quality Knowledge Impulse, project: Toxicity'

向作者/读者索取更多资源

The biota of European rivers are influenced by a variety of stressors, with alterations in hydro-morphology, nutrient enrichment, and toxic substances being the most significant factors. The interaction between these stressors plays a crucial role in influencing the ecological status of the rivers. This highlights the importance of implementing comprehensive management strategies at the catchment scale to achieve good ecological status in European surface waters.
The biota of European rivers are affected by a wide range of stressors impairing water quality and hydro-morphology. Only about 40% of Europe's rivers reach 'good ecological status', a target set by the European Water Framework Directive (WFD) and indicated by the biota. It is yet unknown how the different stressors in concert impact ecological status and how the relationship between stressors and status differs between river types. We linked the intensity of seven stressors to recently measured ecological status data for more than 50,000 sub-catchment units (covering almost 80% of Europe's surface area), which were distributed among 12 broad river types. Stressor data were either derived from remote sensing data (extent of urban and agricultural land use in the riparian zone) or modelled (alteration of mean annual flow and of base flow, total phosphorous load, total nitrogen load and mixture toxic pressure, a composite metric for toxic substances), while data on ecological status were taken from national statutory reporting of the second WFD River Basin Management Plans for the years 2010-2015. We used Boosted Regression Trees to link ecological status to stressor intensities. The stressors explained on average 61% of deviance in ecological status for the 12 individual river types, with all seven stressors contributing considerably to this explanation. On average, 39.4% of the deviance was explained by altered hydro-morphology (morphology: 23.2%; hydrology: 16.2%), 34.4% by nutrient enrichment and 26.2% by toxic substances. More than half of the total deviance was explained by stressor interaction, with nutrient enrichment and toxic substances interacting most frequently and strongly. Our results underline that the biota of all European river types are determined by co-occurring and interacting multiple stressors, lending support to the conclusion that fundamental management strategies at the catchment scale are required to reach the ambitious objective of good ecological status of surface waters.

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