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本文引用的文献

1
Responses of aquatic insects to Cu and Zn in stream microcosms: understanding differences between single species tests and field responses.溪流微宇宙中铜和锌对水生昆虫的响应:理解单物种测试和野外响应之间的差异。
Environ Sci Technol. 2013 Jul 2;47(13):7506-13. doi: 10.1021/es401255h. Epub 2013 Jun 17.
2
A method for deriving water-quality benchmarks using field data.一种利用野外数据推导水质基准的方法。
Environ Toxicol Chem. 2013 Feb;32(2):255-62. doi: 10.1002/etc.2057. Epub 2012 Dec 27.
3
Geologic processes influence the effects of mining on aquatic ecosystems.地质过程影响采矿对水生生态系统的影响。
Ecol Appl. 2012 Apr;22(3):870-9. doi: 10.1890/11-0806.1.
4
Acute toxicity of zinc to several aquatic species native to the Rocky Mountains.几种原产于落基山脉的水生物种对锌的急性毒性。
Arch Environ Contam Toxicol. 2012 Feb;62(2):272-81. doi: 10.1007/s00244-011-9698-3. Epub 2011 Aug 3.
5
Nickel phase partitioning and toxicity in field-deployed sediments.现场部署沉积物中的镍相分配和毒性。
Environ Sci Technol. 2011 Jul 1;45(13):5798-805. doi: 10.1021/es104373h. Epub 2011 Jun 7.
6
Development of a new toxic-unit model for the bioassessment of metals in streams.开发一种新的用于河流中金属生物评估的毒性单位模型。
Environ Toxicol Chem. 2010 Nov;29(11):2432-42. doi: 10.1002/etc.302.
7
Spatial variations in the fate and transport of metals in a mining-influenced stream, North Fork Clear Creek, Colorado.采矿影响河流中金属的归宿和运移的空间变化:科罗拉多州北克里克支流。
Sci Total Environ. 2009 Dec 1;407(24):6223-34. doi: 10.1016/j.scitotenv.2009.08.040. Epub 2009 Oct 3.
8
Influence of remediation in a mine-impacted river: metal trends over large spatial and temporal scales.矿山污染河流修复的影响:大时空尺度上的金属变化趋势
Ecol Appl. 2009 Sep;19(6):1522-35. doi: 10.1890/08-1529.1.
9
Community responses to contaminants: using basic ecological principles to predict ecotoxicological effects.群落对污染物的响应:运用基础生态学原理预测生态毒理学效应
Environ Toxicol Chem. 2009 Sep;28(9):1789-800. doi: 10.1897/09-140.1.
10
Effects of heavy metals on riverine benthic macroinvertebrate assemblages with reference to potential food availability for drift-feeding fishes.重金属对河流底栖大型无脊椎动物群落的影响以及对滤食性鱼类潜在食物可利用性的影响。
Environ Toxicol Chem. 2009 Feb;28(2):354-63. doi: 10.1897/08-200.1.

利用野外和中宇宙实验量化采矿污染溪流中物理和化学应激源的影响

The Use of Field and Mesocosm Experiments to Quantify Effects of Physical and Chemical Stressors in Mining-Contaminated Streams.

作者信息

Cadmus Pete, Clements William H, Williamson Jacob L, Ranville James F, Meyer Joseph S, Gutiérrez Ginés María Jesús

机构信息

Department of Fish, Wildlife and Conservation Biology, Colorado State University , Fort Collins, Colorado 80523, United States.

Colorado Parks and Wildlife, 317 W. Prospect Rd, Fort Collins, Colorado 80526, United States.

出版信息

Environ Sci Technol. 2016 Jul 19;50(14):7825-33. doi: 10.1021/acs.est.6b01911. Epub 2016 Jul 11.

DOI:10.1021/acs.est.6b01911
PMID:27362637
原文链接:https://pmc.ncbi.nlm.nih.gov/articles/PMC5744682/
Abstract

Identifying causal relationships between acid mine drainage (AMD) and ecological responses in the field is challenging. In addition to the direct toxicological effects of elevated metals and reduced pH, mining activities influence aquatic organisms indirectly through physical alterations of habitat. The primary goal of this research was to quantify the relative importance of physical (metal-oxide deposition) and chemical (elevated metal concentrations) stressors on benthic macroinvertebrate communities. Mesocosm experiments conducted with natural assemblages of benthic macroinvertebrates established concentration-response relationships between metals and community structure. Field experiments quantified effects of metal-oxide contaminated substrate and showed significant differences in sensitivity among taxa. To predict the recovery of dominant taxa in the field, we integrated our measures of metal tolerance and substrate tolerance with estimates of drift propensity obtained from the literature. Our estimates of recovery were consistent with patterns observed at downstream recovery sites in the NFCC, which were dominated by caddisflies and baetid mayflies. We conclude that mesocosm and small-scale field experiments, particularly those conducted with natural communities, provide an ecologically realistic complement to laboratory toxicity tests. These experiments also control for the confounding variables associated with field-based approaches, thereby supporting causal relationships between AMD stressors and responses.

摘要

在实地确定酸性矿山排水(AMD)与生态响应之间的因果关系具有挑战性。除了金属含量升高和pH值降低的直接毒理学影响外,采矿活动还通过栖息地的物理改变间接影响水生生物。本研究的主要目标是量化物理(金属氧化物沉积)和化学(金属浓度升高)应激源对底栖大型无脊椎动物群落的相对重要性。用底栖大型无脊椎动物的自然组合进行的中宇宙实验建立了金属与群落结构之间的浓度-响应关系。野外实验量化了金属氧化物污染底物的影响,并显示出不同分类群之间敏感性的显著差异。为了预测野外优势分类群的恢复情况,我们将金属耐受性和底物耐受性的测量结果与从文献中获得的漂移倾向估计值相结合。我们对恢复情况的估计与在NFCC下游恢复地点观察到的模式一致,这些地点以毛翅目昆虫和短脉蜉蝣为主。我们得出结论,中宇宙和小规模野外实验,特别是那些用自然群落进行的实验,为实验室毒性测试提供了生态现实的补充。这些实验还控制了与基于野外的方法相关的混杂变量,从而支持了AMD应激源与响应之间的因果关系。