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利用盐生植物对严重污染的尾矿进行植物稳定化处理以及在田间添加有机和无机改良剂。

Phytostabilisation of severely contaminated mine tailings using halophytes and field addition of organic and inorganic amendments.

作者信息

Pardo T, Bernal M P, Clemente R

机构信息

Department of Soil and Water Conservation and Organic Waste Management, CEBAS-CSIC, PO Box 164, 30100, Murcia, Spain.

Department of Soil and Water Conservation and Organic Waste Management, CEBAS-CSIC, PO Box 164, 30100, Murcia, Spain.

出版信息

Chemosphere. 2017 Jul;178:556-564. doi: 10.1016/j.chemosphere.2017.03.079. Epub 2017 Mar 21.

DOI:10.1016/j.chemosphere.2017.03.079
PMID:28351014
Abstract

Phytostabilisation strategies have proven to be an efficient remediation option for mine tailings, but the adequate plant species and amendments have to be carefully selected. A remediation experiment was carried out at the semi-field level in tailings (pH 3.2, ≈1100, 4700 and 5000 mg kg of As, Pb and Zn, respectively) from the mining district of La Unión-Cartagena (SE Spain). A red mud derivative (Fe/Al oxides), its combination with compost, and hydrated lime (Ca hydroxide) were applied in field plots of 0.25 m. After four months of field stabilisation, tailings were transferred unaltered to a plant growth facility, and Atriplex halimus and Zygophyllum fabago (halophytes) were sown. Three months later, trace element (TE) solubility, plant accumulation and chemical speciation in the tailings pore water were studied. In unamended tailings, soluble TEs concentrations were very high (e.g., 40 mg Zn l), the dominant species being free ions and SO- complexes (>70%). The addition of amendments increased tailings pH (6.7-7), reduced TEs solubility and extractability (>80-99%) and changed the dominant species of soluble Al, Cu, Pb and Zn to hydroxides and/or organo-metallic complexes, but increased slightly the extractable As and soluble Tl concentrations. Plants were able to grow only in amended tailings, and both species presented low levels of Al, As, Cd and Zn. Therefore, the use of combined red mud derivative and compost and halophytes was shown to be a good phytostabilisation strategy, although the dose applied must be carefully chosen in order to avoid possible solubilisation of As and Tl.

摘要

植物稳定化策略已被证明是一种有效的尾矿修复方法,但必须仔细选择合适的植物物种和改良剂。在西班牙东南部拉乌尼翁 - 卡塔赫纳矿区的尾矿(pH值为3.2,砷、铅和锌的含量分别约为1100、4700和5000毫克/千克)上进行了半田间规模的修复实验。在0.25平方米的田间地块中施加了一种赤泥衍生物(铁/铝氧化物)、其与堆肥的混合物以及熟石灰(氢氧化钙)。经过四个月的田间稳定处理后,未改变的尾矿被转移到植物生长设施中,并播种了滨藜和霸王(盐生植物)。三个月后,研究了尾矿孔隙水中微量元素(TE)的溶解度、植物积累量和化学形态。在未改良的尾矿中,可溶性TE的浓度非常高(例如,锌的浓度为40毫克/升),主要形态是自由离子和硫酸根络合物(>70%)。添加改良剂提高了尾矿的pH值(6.7 - 7),降低了TE的溶解度和可提取性(>80 - 99%),并将可溶性铝、铜、铅和锌的主要形态转变为氢氧化物和/或有机金属络合物,但略微增加了可提取砷和可溶性铊的浓度。植物仅能在改良后的尾矿中生长,且两种植物的铝、砷、镉和锌含量都较低。因此,使用赤泥衍生物与堆肥的混合物以及盐生植物被证明是一种良好的植物稳定化策略,尽管必须仔细选择施用剂量以避免砷和铊可能的溶解。

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