Department of Biology, Wilfrid Laurier University, Waterloo, Ontario, Canada.
Canadian Rivers Institute, University of New Brunswick, Fredericton, New Brunswick, Canada.
Integr Environ Assess Manag. 2024 May;20(3):616-644. doi: 10.1002/ieam.4823. Epub 2023 Sep 6.
Environmental impact assessment (EIA) has been widely criticized by the aquatic science community for poorly aligned approaches when selecting endpoints and collecting data during the baseline, predictive modeling, and postdevelopment monitoring phases. If these critical phases of the EIA process are not aligned properly, it can be difficult to evaluate the presence of postdevelopment effects. Examples of the misalignment of these phases include baseline studies failing to measure indicators that are monitored postdevelopment; predictive assessments that do not quantitatively predict conditions or potential impacts postdevelopment; and the failure to identify relevant indicators that may detect effects postdevelopment. For aquatic assessments, understanding how to protect critical ecosystem attributes to satisfy regulatory concerns could help to better align aquatic science monitoring activities across EIA phases. In this article we investigate recent Canadian hydroelectric dam EIAs to evaluate how well recent assessment approaches are meeting these necessary conditions of good aquatic EIA practice through the lens of ecosystem services from a fish's perspective. We found that larger facilities generally had baseline studies and modeling that better supported postdevelopment monitoring, but improvements in structure, linkages, and expectations would better align EIA phases in a manner that would improve assessments and environmental protection. Integr Environ Assess Manag 2024;20:616-644. © 2023 The Authors. Integrated Environmental Assessment and Management published by Wiley Periodicals LLC on behalf of Society of Environmental Toxicology & Chemistry (SETAC).
环境影响评估 (EIA) 在选择终点和收集基线、预测建模和开发后监测阶段的数据时,方法与水生科学社区的要求不一致,因此受到了广泛批评。如果 EIA 过程的这些关键阶段没有正确对齐,就很难评估开发后的影响。这些阶段不对齐的例子包括基线研究未能测量开发后监测的指标;预测评估不能定量预测开发后的条件或潜在影响;以及未能确定可能检测到开发后影响的相关指标。对于水生评估,了解如何保护关键生态系统属性以满足监管关注,可以帮助更好地在 EIA 各阶段对齐水生科学监测活动。在本文中,我们研究了最近的加拿大水电大坝 EIA,从鱼类的角度评估了最近的评估方法如何通过生态系统服务来满足良好的水生 EIA 实践的这些必要条件。我们发现,较大的设施通常具有更好地支持开发后监测的基线研究和建模,但结构、联系和期望的改进将以改善评估和环境保护的方式更好地对齐 EIA 各阶段。