Conesa Héctor M, Schulin Rainer
Institute of Terrestrial Ecosystems, ETH Zurich, Universitaetstrasse 16, CH-8092, Zürich, Switzerland.
J Environ Monit. 2010 Jun;12(6):1225-33. doi: 10.1039/c000346h. Epub 2010 Apr 14.
After mining in the Cartagena-La Unión Mining District (SE Spain) was discontinued in 1992, various studies have shown that large amounts of toxic metals continue to be transferred with the spread of unstabilized mining wastes to the nearby ecosystems. Local creeks seem to be important pathways carrying eroded materials from the headwaters to the nearby coastal areas of the Mediterranean Sea. Studies have shown the presence of high metal concentrations in the sediments of riverbeds and in river mouths and adjacent coastal marshes (e.g. 500 mg kg(-1) As; 12 000 mg kg(-1) Pb). Also, some nearby agricultural areas are affected (up to 10 mg kg(-1) Pb in lettuce leaves). Metal transfer into biota has been demonstrated in creek sediments in relation to benthic organisms (up to 222 mg kg(-1) Pb in molluscs). The mining wastes in the area are spontaneously colonized by native plant species. On the tailings, most of the plant species are grasses (e.g. Lygeum spartum, Piptatherum miliaceum); in polluted salt marshes, halophytic species dominate (e.g. Arthrocnemum macrostachyum). Metal uptake by plants is in general low (10 mg kg(-1) for Cu; <200 mg kg(-1) Pb; <500 mg kg(-1) Zn). Preliminary tests have shown the suitability of amendments (e.g. lime, fertilizer, pig manure) to improve the establishment of certain vegetation on the tailings. Phytostabilization appears to be a promising technology to decrease erosion in the tailings. However, tailings must be individually analysed in order to determine their geostructural stability, as in addition, mechanical stabilization will be needed in some cases to prevent collapse.
1992年卡塔赫纳-拉乌尼翁矿区(西班牙东南部)停止采矿后,各项研究表明,随着未稳定化的采矿废弃物扩散至附近生态系统,大量有毒金属仍在持续转移。当地的小溪似乎是将侵蚀物质从源头输送至地中海附近沿海地区的重要通道。研究表明,河床沉积物、河口及邻近沿海沼泽中存在高浓度金属(例如,砷含量为500毫克/千克;铅含量为12000毫克/千克)。此外,一些附近的农业区也受到影响(生菜叶中的铅含量高达10毫克/千克)。金属向生物群的转移已在与底栖生物相关的小溪沉积物中得到证实(软体动物中的铅含量高达222毫克/千克)。该地区的采矿废弃物被本地植物物种自然定殖。在尾矿上,大多数植物物种为禾本科植物(例如,硬叶针茅、粟草);在受污染的盐沼中,盐生植物占主导(例如,盐节木)。植物对金属的吸收总体较低(铜为10毫克/千克;铅小于200毫克/千克;锌小于500毫克/千克)。初步试验表明,改良剂(例如石灰、肥料、猪粪)适用于改善尾矿上某些植被的生长。植物稳定化似乎是一种减少尾矿侵蚀的有前景的技术。然而,必须对尾矿进行单独分析以确定其地质结构稳定性,此外,在某些情况下还需要进行机械稳定化以防止坍塌。