Kim Ju-Yong, Lee Byung-Tae, Shin Kyung-Hee, Lee Kun-Young, Kim Kyoung-Woong, An Kwang-Guk, Park Young-Seok, Kim Jeong-Yeon, Kwon Young-Ho
Department of Environmental Science and Engineering and International Environmental Research Center (IERC), GIST, Gwangju 500-712, South Korea.
Environ Monit Assess. 2007 Jun;129(1-3):79-85. doi: 10.1007/s10661-006-9429-9. Epub 2006 Oct 21.
Ecological health in a temperate stream impacted by acid mine drainage (AMD) was evaluated by using a multimetric approach of the Index of Biological Integrity (IBI) based on natural fish assemblage. Recently, this approach has been widely used in many developed countries as a tool for ecological risk assessments of water environments. We used 10 metric systems, instead of 12 metrics suggested by Barbour, M. T., Gerritsen, J., Snyder, B. D., & Stribling, J. B. (1999). Rapid Bioassessment Protocols for Use in Streams and Wadeable Rivers: Periphyton, benthic Macroinvertebrates and Fish, 2nd edn. EPA 841-B-99-002. Washington, DC: U.S. Environmental Protection Agency, Office of Water, for a development of the regional IBI model, and used trophic guilds, habitat guilds, and richness variables for the calculation of IBI values. In the model, the attributes of four of 11 metrics were modified for the regional application. IBI values in the stream averaged 20.6 (n = 5), indicating a "poor condition" in terms of ecological health according to the modified criteria of U.S. EPA (1993). Fish Field and Laboratory Methods for Evaluating the Biological Integrity of Surface Waters. EPA 600-R-92-111. Environmental Monitoring systems Laboratory - Cincinnati office of Modeling, Monitoring systems, and quality assurance Office of Research Development, U.S. EPA, Cincinnati, Ohio, 45268. In particular, mean IBI values in the impacted areas of sites 2 and 3 were 13, and this health condition was categorized as "very poor condition." IBI values in the impacted sites were significantly lower than the values found in the control. Also, we found that fishes in site sites 2 and 3 were not present during the study, and morphological deformity of Rhynchocypris oxycephalus was observed in site 4, influenced directly by sites 2 and 3, indicating a chemical impact in the sites. From the results of experiments in which AMD was treated with marine shells at stagnant condition, pH increased up to 6.0 from 3.1, and Fe and Al were removed up to 99% within 6 h. In the reactor experiment considering field application, pH of effluent maintained around 7.0. In addition, concentrations of Fe, Al, and heavy metals decreased remarkably in the effluents, and bottom-opened screen between neutralizer basins showed high effectiveness in the treatment of AMD.
利用基于天然鱼类群落的生物完整性指数(IBI)多指标方法,对受酸性矿山排水(AMD)影响的温带溪流的生态健康状况进行了评估。最近,这种方法在许多发达国家被广泛用作水环境生态风险评估的工具。我们使用了10个指标体系,而不是Barbour、M. T.、Gerritsen、J.、Snyder、B. D.和Stribling、J. B.(1999年)建议的12个指标。《用于溪流和可涉渡河流的快速生物评估协议:周丛生物、底栖大型无脊椎动物和鱼类》,第2版。EPA 841-B-99-002。华盛顿特区:美国环境保护局水办公室,用于开发区域IBI模型,并使用营养类群、栖息地类群和丰富度变量来计算IBI值。在该模型中,对11个指标中的4个指标的属性进行了修改以用于区域应用。溪流中的IBI值平均为20.6(n = 5),根据美国环境保护局(1993年)的修改标准,这表明生态健康状况“较差”。《评估地表水生物完整性的鱼类现场和实验室方法》。EPA 600-R-92-111。环境监测系统实验室 - 辛辛那提建模、监测系统和质量保证办公室,美国环境保护局研究与开发办公室,俄亥俄州辛辛那提,45268。特别是,第2和第3站点受影响区域的平均IBI值为13,这种健康状况被归类为“非常差的状况”。受影响站点的IBI值显著低于对照站点的值。此外,我们发现在研究期间第2和第3站点没有鱼类,并且在第4站点观察到尖头鱥的形态畸形,该站点直接受第2和第3站点影响,表明这些站点存在化学影响。在静止条件下用海贝壳处理AMD的实验结果表明,pH值从3.1升高到6.0,并且铁和铝在6小时内去除率高达99%。在考虑现场应用情况的反应器实验中,流出物的pH值保持在7.0左右。此外,流出物中铁、铝和重金属的浓度显著降低,中和池之间的底部开口筛网在AMD处理中显示出高效性。