首页> 外文期刊>Applied Geochemistry: Journal of the International Association of Geochemistry and Cosmochemistry >Hydrochemistry, mineralogy and sulfur isotope geochemistry of acid mine drainage at the Mt. Morgan mine environment, Queensland, Australia
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Hydrochemistry, mineralogy and sulfur isotope geochemistry of acid mine drainage at the Mt. Morgan mine environment, Queensland, Australia

机译:山顶酸性矿山排水的水化学,矿物学和硫同位素地球化学。澳大利亚昆士兰州的摩根矿山环境

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摘要

Mineralogical, hydrochemical and S isotope data were used to constrain hydrogeochemical processes that produce acid mine drainage from sulfidic waste at the historic Mount Morgan Au-Cu mine, and the factors controlling the concentration of SO4 and environmentally hazardous metals in the nearby Dee River in Queensland, Australia. Some highly contaminated acid waters, with metal contents up to hundreds of orders of magnitude greater than the Australia-New Zealand environmental standards, by-pass the water management system at the site and drain into the adjacent Dee River.Mine drainage precipitates at Mt. Morgan were classified into 4 major groups and were identified as hydrous sulfates and hydroxides of Fe and Al with various contents of other metals. These minerals contain adsorbed or mineralogically bound metals that are released into the water system after rainfall events. Sulfate in open pit water and collection sumps generally has a narrow range of S isotope compositions (delta(34)S = 1.8-3.7 parts per thousand) that is comparable to the orebody sulfides and makes S isotopes useful for tracing SO4 back to its source. The higher delta(34)S values for No. 2 Mill Diesel sump may be attributed to a difference in the source. Dissolved SO4 in the river above the mine influence and 20 km downstream show distinctive heavier isotope compositions (delta(34)S = 5.4-6.8 parts per thousand). The Dee River downstream of the mine is enriched in S-34 (delta(34)S = 2.8-5.4 parts per thousand) compared with mine drainage possibly as a result of bacterial SO4 reduction in the weir pools, and in the water bodies within the river channel. The SO4 and metals attenuate downstream by a combination of dilution with the receiving waters, SO4 reduction, and the precipitation of Fe and Al sulfates and hydroxides. It is suggested here that in subtropical Queensland, with distinct wet and dry seasons, temporary reducing environments in the river play an important role in S isotope systematics. (c) 2004 Elsevier Ltd. All rights reserved.
机译:利用矿物学,水化学和S同位素数据来约束水文地球化学过程,这些过程从历史悠久的摩根山金铜矿山的硫化物废物中产生酸性矿山排水,以及控制昆士兰州迪河附近SO4和环境有害金属浓度的因素,澳大利亚。某些高度污染的酸性水(其金属含量比澳大利亚-新西兰的环境标准高出数百个数量级)绕过现场的水管理系统并排入相邻的迪河(Dee River)。摩根分为四大类,被识别为铁和铝的含水硫酸盐和氢氧化物,以及其他金属的含量各不相同。这些矿物质包含吸附或矿物结合的金属,降雨后这些金属会释放到水系统中。露天矿井和集水坑中的硫酸盐通常具有较窄的S同位素组成范围(δ(34)S = 1.8-3.7千分之一),与矿石体中的硫化物相当,并使S同位素可用于追踪SO4的来源。 2号柴油机油底壳的较高delta(34)S值可能归因于来源上的差异。在矿井影响上方的河流中和下游20 km处溶解的SO4显示出独特的重同位素组成(δ(34)S = 5.4-6.8千分之几)。与矿山排水相比,矿山下游的迪河富集了S-34(δ(34)S = 2.8-5.4千分之一),这可能是由于堰池以及其内水体中的细菌SO4减少所致河道。 SO4和金属通过与接收水稀释,SO4还原以及铁,铝硫酸盐和氢氧化物的沉淀相结合而向下游衰减。建议在亚热带的昆士兰州,具有不同的干湿季节,河流中的临时还原环境在S同位素系统中起着重要的作用。 (c)2004 Elsevier Ltd.保留所有权利。

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