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Fast formation of supergene Mn oxides/hydroxides under acidic conditions in the oxic/anoxic transition zone of a shallow aquifer

机译:在酸性条件下在浅层含水层的含氧/缺氧过渡带中快速生成表皮锰氧化物/氢氧化物

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摘要

Extensive uranium mining in the former German Democratic Republic (GDR) in eastern Thuringia and Saxony took place during the period of 1946-1990. During mining activities, pelitic sediments rich in organic carbon and uranium were processed and exposed to oxygen. Subsequent pyrite oxidation and acidic leaching lead to partial contamination of the area with heavy metals and acid mine drainage (AMD) even few years after completion of remediation. One of those areas is the former heap Gessen (Ronneburg, Germany) were the residual contamination can be found 10 m under the base of the former heap containing partly permeable drainage channels. Actually, in such a system, a rapid but locally restricted mineralization of Mn oxides takes place under acidic conditions. This formation can be classified as a natural attenuation process as certain heavy metals, e.g., Cd (up to 6 mu g/g), Ni (up to 311 mu g/g), Co (up to 133 mu g/g), and Zn (up to 104 mu g/g) are bound to this phases. The secondary minerals occur as colored layers close to the shallow aquifer in glacial sediments and could be identified as birnessite and todorokite as Mn phase. The thermodynamic model shows that even small changes in the system are sufficient to shift either the pH or the Eh in the direction of stable Mn oxide phases in this acidic system. As a consequence of 9-15-year-long formation process (or even less), the supergene mineralization provides a cost-efficient contribution for remediation (natural attenuation) strategies of residual with heavy metals (e.g., Cd, Co, Ni, Zn) contaminated substrates.
机译:1946-1990年期间,前德意志民主共和国(GDR)在图林根州东部和萨克森州进行了广泛的铀矿开采。在采矿活动中,处理了富含有机碳和铀的胶质沉积物,并将其暴露在氧气中。随后的黄铁矿氧化和酸性浸出,甚至在整治数年后,仍会因重金属和酸性矿井排水(AMD)对该区域造成部分污染。这些区域之一是前堆Gessen(德国罗讷堡),其残留污染物可在前堆底部10 m处发现,其中包含部分可渗透的排水通道。实际上,在这样的系统中,在酸性条件下会发生快速但局部受限制的锰氧化物矿化。这种形成可以归类为自然衰减过程,例如某些重金属,例如Cd(最高6μg/ g),Ni(最高311μg/ g),Co(最高133μg/ g), Zn(最高104μg/ g)与该相结合。次生矿物以接近冰层浅层含水层的有色层的形式出现,可以被识别为水钠锰矿和钙锰矿为Mn相。热力学模型表明,即使系统发生很小的变化也足以使该酸性系统中的pH值或Eh沿稳定的Mn氧化物相方向移动。由于9-15年的形成过程(甚至更少),超基因矿化为残留重金属(例如Cd,Co,Ni,Zn等)的修复(自然衰减)策略提供了具有成本效益的贡献。 )受污染的基材。

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