Kraus Uta, Wiegand Jens
Faculty Biology and Geography, University of Duisburg-Essen, Universitaetsstrasse 2, 45141 Essen, Germany.
Sci Total Environ. 2006 Aug 31;367(2-3):855-71. doi: 10.1016/j.scitotenv.2005.12.027. Epub 2006 Feb 24.
In 1998, a toxic spill from a pyrite mine (Aznalcóllar, SW Spain) contaminated some 40 km2 of the Agrio and Guadiamar river valley with heavy metal-enriched tailings sludge and acidic mine water. The aim of this study is to describe the long-term effects of heavy metal migration particularly with respect to the extent of vertical redistribution of As, Cd, Cu, Fe, Pb, S, Sb and Zn in soils and sediments of the river Guadiamar 4 years after the accident. For an assessment of the mobility behaviour, chemical associations of Cu, Pb, Sb and Zn in depth profiles polluted by tailings were determined by using sequential extraction procedures. In 2002, residues of toxic tailings were found in several places along the river Guadiamar. Heavy weathering has accelerated heavy metal displacement and contamination of the surrounding soil. Two element groups of contrary mobility can be distinguished: Cd and Zn are highly mobile and show strong displacements in acidic surroundings. Accumulation zones for Cd and Zn develop in less acidic soil layers due to the occurrence of Fe oxides, which constitute retaining fractions for these elements. The immobile elements Pb and Sb represent the second group. Highest concentrations of Pb and Sb are found in the tailings sludge. Cu and As show a variable distribution pattern. As a consequence of the heavy metal migration, an accumulation zone has formed up to 30 cm into the underlying soil at the time of investigation. In the future, there may be further penetration of heavy metals to greater depths.
1998年,西班牙西南部阿兹纳科利亚尔的一座黄铁矿矿场发生有毒物质泄漏,约40平方公里的阿格里奥河和瓜迪亚马尔河谷被富含重金属的尾矿污泥和酸性矿井水污染。本研究的目的是描述事故发生4年后,重金属迁移的长期影响,特别是关于瓜迪亚马尔河中土壤和沉积物中砷、镉、铜、铁、铅、硫、锑和锌的垂直再分布程度。为了评估迁移行为,通过连续萃取程序确定了尾矿污染深度剖面中铜、铅、锑和锌的化学结合形态。2002年,在瓜迪亚马尔河沿岸的几个地方发现了有毒尾矿的残留物。剧烈的风化加速了重金属的迁移和对周围土壤的污染。可以区分出两组迁移性相反的元素:镉和锌具有高度迁移性,在酸性环境中表现出强烈的迁移。由于铁氧化物的存在,镉和锌的积累区出现在酸性较弱的土壤层中,铁氧化物构成了这些元素的保留部分。不迁移的元素铅和锑代表第二组。铅和锑的最高浓度出现在尾矿污泥中。铜和砷呈现出可变的分布模式。由于重金属的迁移,在调查时,在下层土壤中已形成了一个深度达30厘米的积累区。未来,重金属可能会进一步渗透到更深的深度。