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Biomonitoring of intermittent rivers and ephemeral streams in Europe: Current practice and priorities to enhance ecological status assessments

机译:欧洲间歇性河流和短暂河流的生物监测:加强生态状况评估的当前做法和重点

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摘要

Intermittent rivers and ephemeral streams (IRES) are common across Europe and dominate some Mediterranean river networks, supportinghigh biodiversity and providing ecosystem services in all climate zones.As dynamic ecosystems that transition between flowing, pool, and dry states, IRES are typically poorly represented in biomonitoring programmes implemented to characterize EU Water Framework Directive 'ecologicalstatus'. We report the results of a survey completed by representatives from 20 European countries to document national IRES biomonitoring activity. We identify five major barriers to effective ecological statusclassification in IRES: 1. the exclusion of IRES from Water Framework Directive biomonitoring based on their small catchment size; 2. the lack of river typologies that distinguish between contrasting IRES; 3.difficulties in defining the 'reference conditions' that represent unimpacted dynamic ecosystems; 4. classification of IRES ecological status based on lotic communities sampled using methods developed forperennial rivers; and 5. a reliance on taxonomic characterization oflocal communities. Despite these challenges, we recognize examples ofinnovative practice that can inform modification of current biomonitoringactivity to promote effective IRES status classification. Priorities for future research include the reconceptualization of the reference condition approach to accommodate spatiotemporal fluctuations incommunity composition, and modification of indices of ecosystem health torecognize taxon-specific sensitivity to intermittence and dispersal abilities, within a landscape context.
机译:断断续续的河流和短暂河流(IRES)在整个欧洲很常见,并且在地中海的一些河网中占主导地位,在所有气候区中都支持较高的生物多样性并提供生态系统服务。作为在水流状态,池水状态和干旱状态之间转换的动态生态系统,IRES的代表性通常很差实施生物监测计划,以表征欧盟水框架指令的“生态状况”。我们报告了由20个欧洲国家的代表完成的一项调查结果,以记录国家IRES生物监测活动。我们确定了IRES中有效的生态状况分类的五个主要障碍:1.根据流域面积小,将IRES从水框架指令生物监测中排除; 2.缺乏区分不同IRES的河流类型; 3定义代表未受影响的动态生态系统的``参考条件''的困难; 4.根据使用多年生河流开发的方法抽样的抽水群落对IRES生态状况进行分类; 5.依靠当地社区的分类学特征。尽管存在这些挑战,但我们认识到一些创新实践的实例,这些实例可以指导当前生物监测活动的修改,以促进有效的IRES状态分类。未来研究的重点包括重新构想参考条件方法,以适应社区组成的时空波动,以及修改生态系统健康指数,以在景观环境中识别分类群对间断和分散能力的敏感性。

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