Griffith Michael B, McManus Michael G
U. S. Environmental Protection Agency, Office of Research and Development, National Center for Environmental Assessment, Cincinnati, Ohio.
Current affiliation: U. S. Environmental Protection Agency, Office of Research and Development, Center for Environmental Measurement and Modeling, Cincinnati, Ohio.
River Res Appl. 2020 Oct;36(8):1398-1415. doi: 10.1002/rra.3694. Epub 2020 Aug 23.
Stream and river restoration practices have become common in many parts of the world. To answer the question whether such restoration measures improve freshwater biotic assemblages or functions over time, and if not, can general reasons be identified for such outcomes, we conducted a literature survey and review of studies in which different types of stream restorations were conducted and outcomes assessed. In the first paper, we reviewed studies of culvert restorations, acid mine drainage or industrial pollution restoration; and urban stream restoration projects. Here, we review studies of restoration via dam removal, changes in dam operation or fish passage structures; instream habitat modification; riparian restoration or woody material addition; channel restoration and multiple restoration measures and develop some general conclusions from these reviews. Biomonitoring in different studies detected improvements for some restoration measures; other studies found minimal or no statistically significant increases in biotic assemblage richness, abundances or functions. In some cases, untreated stressors may have influenced the outcomes of the restoration, but in many cases, there were mismatches in the temporal or spatial scale of the restoration measure undertaken and associated monitoring. For example, either biomonitoring to measure restoration effects was conducted over a too short a time period after restoration for effects to be observed, or the sources and stressors needing remediation occurred at a larger catchment scale than the restoration. Also, many restoration measures lack observations from unimpaired reference sites for use in predicting how much of a beneficial effect might be expected.
溪流和河流修复措施在世界许多地方已变得很常见。为了回答这些修复措施是否会随着时间推移改善淡水生物群落或功能,以及如果没有改善,能否找出导致这种结果的一般原因,我们对进行了不同类型溪流修复并评估了结果的研究进行了文献调查和综述。在第一篇论文中,我们综述了涵管修复、酸性矿山排水或工业污染修复以及城市溪流修复项目的研究。在此,我们综述了通过拆除大坝、改变大坝运行方式或修建鱼类洄游结构进行修复、改善河道内栖息地、河岸修复或添加木质材料、河道修复以及多种修复措施的研究,并从这些综述中得出一些一般性结论。不同研究中的生物监测发现某些修复措施有改善效果;其他研究则发现生物群落丰富度、丰度或功能在统计学上几乎没有显著增加或根本没有增加。在某些情况下,未处理的压力源可能影响了修复结果,但在许多情况下,所采取的修复措施的时间或空间尺度与相关监测之间存在不匹配。例如,要么用于测量修复效果的生物监测在修复后进行的时间过短,以至于无法观察到效果,要么需要修复的污染源和压力源发生的集水区尺度大于修复区域。此外,许多修复措施缺乏来自未受损害的参照地点的观测数据,无法用于预测可能预期的有益效果程度。