首页> 外文期刊>European Journal of Ecology >Ecological modelling of a wetland for phytoremediating Cu, Zn and Mn in a gold–copper mine site using Typha domingensis (Poales: Typhaceae) near Orange, NSW, Australia
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Ecological modelling of a wetland for phytoremediating Cu, Zn and Mn in a gold–copper mine site using Typha domingensis (Poales: Typhaceae) near Orange, NSW, Australia

机译:澳大利亚新南威尔士州奥兰治附近的金铜矿场湿地生态修复植物铜,锌和锰的生态建模,使用的是香蒲(香蒲:香蒲科)

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An artificial wetland was computationally modelled using STELLA?, a graphical programming tool for an Au-Cu mine site in Central-west NSW, the aim of which was to offer a predictive analysis of a proposed wetland for Cu, Zn and Mn removal using Typha domingensis as the agent. The model considers the important factors that impact phytoremediation of Cu, Zn and Mn. Simulations were performed to optimise the area of the wetland; concentration of Cu, Zn and Mn released from mine (AMD); and flow rates of water for maximum absorption of the metals. A scenario analysis indicates that at AMD = 0.75mg/L for Cu, Zn and Mn, 12.5, 8.6, and 357.9 kg of Cu, Zn and Mn, respectively, will be assimilated by the wetland in 35 years, which would be equivalent to 61 mg of Cu/kg, 70 mg of Zn/kg and 2,886 mg of Mn/kg of T. domingensis, respectively. However, should Cu, Zn and Mn in AMD increase to 3 mg/L, then 18.6 kg of Cu and 11.8 kg of Zn, respectively, will be assimilated in 35 years, whereas no substantial increase in absorption for Mn would occur. This indicates that 91 mg of Cu, 96 mg of Zn and 2917 mg of Mn will be assimilated for every kg of T. domingensis in the wetland. The best option for Cu storage would be to construct a wetland of 50,000 m~(2) area (AMD = 0.367 mg/L of Cu), which would capture 14.1 kg of Cu in 43 years, eventually releasing only 3.9 kg of Cu downstream. Simulations performed for a WA of 30,000 m~(2) indicate that for AMD = 0.367 mg/L of Zn, the wetland captures 6.2 kg, releasing only 3.5 kg downstream after 43 years; the concentration of Zn in the leachate would be 10.2 kg, making this the most efficient wetland amongst the options considered for phytoremediating Zn. This work will help mine managers and environmental researchers in developing an effective environmental management plan by focusing on phytoremediation, with a view at extracting Cu, Zn and Mn from the contaminated sites.
机译:使用STELLA?(一种用于新南威尔士州中西部Au-Cu矿山的图形编程工具)对人工湿地进行了计算建模,其目的是对拟议的湿地中使用香蒲去除Cu,Zn和Mn进行预测分析domingensis作为代理。该模型考虑了影响铜,锌和锰植物修复的重要因素。进行了模拟以优化湿地面积;矿山释放的铜,锌和锰的浓度(AMD);和水的流速以最大程度地吸收金属。情景分析表明,在AMD = 0.75mg / L的铜,锌和锰下,湿地在35年内将分别吸收12.5、8.6和357.9 kg的铜,锌和锰,这相当于多明镰刀菌分别为61 mg铜/ kg,70 mg锌/ kg和2886 mg Mn / kg。但是,如果AMD中的Cu,Zn和Mn增加到3 mg / L,则35年内将分别吸收18.6 kg的铜和11.8 kg的锌,而Mn的吸收不会出现实质性的增加。这表明在湿地中,每千克多明红豆杉将吸收91 mg的铜,96 mg的锌和2917 mg的锰。储存铜的最佳选择是建造一个50,000 m〜(2)面积的湿地(AMD = 0.367 mg / L的铜),该湿地将在43年内捕获14.1 kg的铜,最终仅释放3.9 kg的铜。对30,000 m〜(2)的WA进行的模拟表明,对于AMD =锌的0.367 mg / L,湿地捕获6.2 kg,43年后仅释放3.5 kg。渗滤液中Zn的浓度为10.2 kg,使其成为考虑植物修复Zn的最有效的湿地。这项工作将专注于植物修复,从而帮助矿山管理者和环境研究人员制定有效的环境管理计划,以期从受污染的地点提取铜,锌和锰。

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