Gandy C J, Smith J W N, Jarvis A P
Hydrogeochemical Engineering Research and Outreach (HERO), Institute for Research on Environment and Sustainability, Newcastle University, Newcastle upon Tyne, NE1 7RU, UK.
Sci Total Environ. 2007 Feb 15;373(2-3):435-46. doi: 10.1016/j.scitotenv.2006.11.004. Epub 2006 Dec 13.
Mine water pollution is a major cause of surface- and groundwater pollution in former mining districts throughout Europe. It is a potential barrier to achieving good status water bodies, which is a requirement of the EU Water Framework Directive. In the UK, a concerted effort has been made over the last decade or so to address the scientific and practical challenges relating to the remediation of mine water pollution. However, most of this work has focused on remediation of point sources of pollution (typically arising from abandoned mines and shafts), while the behaviour of mine water at the groundwater-surface water interface (the "hyporheic zone") has received far less attention in relevant scientific and engineering literature. The extent of mine water pollution and capacity for its attenuation at the hyporheic zone has not been well quantified while, furthermore, the complex chemical and microbial processes occurring there (specifically with reference to mining-derived pollutants) have not been investigated in any depth. The absence of such data may relate, in a large part, to the difficulty in physically measuring volumes and concentrations associated with these river inputs/exports. A far greater body of literature addresses biogeochemical processes at the hyporheic zone (especially relating to manganese), albeit many such articles relate to aqueous metal dynamics in general, rather than mine water specifically. This paper presents a review of the natural attenuation processes that may limit the movement and availability of mining-derived pollutants at the groundwater-surface water (GW-SW) interface, and specifically within the hyporheic zone. A substantial part focuses on precipitation and adsorption processes at the hyporheic zone, as well as discussing the role of microbial processes in governing metal ion mobility.
矿井水污染是欧洲各地原矿区地表水和地下水污染的主要原因。这是实现水体良好状态的一个潜在障碍,而水体良好状态是欧盟水框架指令的一项要求。在英国,在过去十年左右的时间里,人们齐心协力应对与矿井水污染修复相关的科学和实际挑战。然而,这项工作大多集中在污染点源(通常来自废弃矿井和竖井)的修复上,而矿井水在地下水与地表水界面(“河溪带”)的行为在相关科学和工程文献中受到的关注要少得多。矿井水污染的程度及其在河溪带的衰减能力尚未得到很好的量化,此外,在那里发生的复杂化学和微生物过程(特别是与采矿产生的污染物有关的过程)也没有得到深入研究。缺乏这些数据在很大程度上可能与实际测量与这些河流输入/输出相关的水量和浓度的困难有关。尽管许多关于河溪带生物地球化学过程(特别是与锰有关的过程)的文章通常涉及水相金属动力学,而不是专门针对矿井水,但关于这方面的文献要多得多。本文综述了可能限制采矿产生的污染物在地下水与地表水(GW - SW)界面,特别是在河溪带内的迁移和可利用性的自然衰减过程。其中很大一部分内容聚焦于河溪带的沉淀和吸附过程,并讨论了微生物过程在控制金属离子迁移率方面的作用。