Kotalik Christopher J, Cadmus Pete, Clements William H
Department of Fish, Wildlife and Conservation Biology, Colorado State University, Fort Collins, CO 80521, USA.
Department of Fish, Wildlife and Conservation Biology, Colorado State University, Fort Collins, CO 80521, USA; Aquatic Research, Colorado Parks and Wildlife, Fort Collins, CO 80526, USA.
Sci Total Environ. 2021 Jun 1;771:145419. doi: 10.1016/j.scitotenv.2021.145419. Epub 2021 Jan 27.
Mineral extraction has resulted in widespread stream impairment due to habitat degradation and water quality impacts from acid mine drainage (AMD). The North Fork of Clear Creek (NFCC), Colorado, USA was historically impaired by AMD from two major point-source inputs, with some stream segments devoid of aquatic life prior to remediation. In the summer of 2017, the North Clear Creek Water Treatment Plant (NCCWTP) began AMD water treatment. To predict and characterize the biological recovery of NFCC to improvements in water quality, we conducted stream mesocosm and field experiments, as well as biomonitoring of benthic communities using a Before-After Control-Impact (BACI) study design. The NFCC stream community responded rapidly to improved water quality. Benthic algal biomass increased at impacted sites and macroinvertebrate surveys showed significant increases in abundance, taxa richness, and emerging adult aquatic insects. However, the dominant taxa colonizing downstream segments of NFCC differed considerably from those predicted based on previous field and experimental results. We hypothesize that this discrepancy is the result of differences in metal exposure regimes observed between our field and mesocosm approaches (i.e., fluctuating vs stable), colonization attributes (i.e., open vs closed system), and spatiotemporal differences in metal sensitivity due to macroinvertebrate phenology. We expect continued biological recovery in NFCC, but habitat impairment and residual sources of metals will continue to impair aquatic life until those stressors abate. Applying a combination of controlled experimental and BACI field approaches to predict and evaluate AMD-remediation projects in the future will improve the ability to understand the physical, chemical, and biological mechanisms influencing stream recovery.
由于栖息地退化以及酸性矿山排水(AMD)对水质的影响,矿产开采已导致广泛的溪流受损。美国科罗拉多州清澈溪北支流(NFCC)历史上受到来自两个主要点源输入的AMD影响,在修复之前,一些溪段没有水生生物。2017年夏天,北清澈溪水处理厂(NCCWTP)开始对AMD进行水处理。为了预测和描述NFCC水质改善后的生物恢复情况,我们进行了溪流中宇宙和野外实验,以及使用前后对照影响(BACI)研究设计对底栖生物群落进行生物监测。NFCC溪流群落对水质改善反应迅速。受影响地点的底栖藻类生物量增加,大型无脊椎动物调查显示丰度、分类群丰富度和新兴成年水生昆虫显著增加。然而,在NFCC下游段定殖的优势分类群与根据先前的野外和实验结果预测的分类群有很大差异。我们假设这种差异是由于我们的野外和中宇宙方法之间观察到的金属暴露模式差异(即波动与稳定)、定殖属性(即开放与封闭系统)以及由于大型无脊椎动物物候导致的金属敏感性时空差异造成的。我们预计NFCC将继续实现生物恢复,但栖息地受损和金属残留源将继续损害水生生物,直到这些压力源减轻。未来应用受控实验和BACI野外方法相结合来预测和评估AMD修复项目,将提高理解影响溪流恢复的物理、化学和生物机制的能力。