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Leachability of 17-year old stabilised/solidified contaminated site soils

机译:17岁的稳定/固化污染场地土壤的可浸性

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Increased acceptance of in-situ stabilisation/solidification (S/S) depends on its long-term effectiveness and field performance at contaminated sites. Field trials of deep soil mixing application of S/S were performed at a contaminated site in West Drayton, near Heathrow Airport, in the UK back in 1996. Core samples were taken from this site at 2 months and 4.5 years and tested. This paper addresses the leaching properties of the contaminated site soils at 17 years in comparison to the properties at 0.24, 2.4 and 5 years. Seven different cement-based binders were used, including cement, PFA, lime and bentonite to the soils which were contaminated with a cocktail of heavy metals and organics. Two leaching methods: Toxicity Characteristic Leaching Procedure (TCLP) and the BS EN 12457 were applied to study the leaching behaviour of the heavy metals in stablised/solidified soils. The leaching test results showed that leachate pH decreased with time in the first 5 years and then leveled off at 17 years. The BS EN 12457 leachate concentrations were lower than drinking water standards, suggesting that the performance of the S/S at 17 years' service time is satisfactory. The leaching behaviour of the heavy metals in these S/S soils was mainly controlled by the alkalinity of the binders, with some of these heavy metals being absorbed into calcium silicate hydrates (C-S-H) gel phases. The binding mechanisms within the applied cementitious binders may be dominated by their leachate pH which correlated with their corresponding metal hydroxide solubility.
机译:原位稳定化/固化(S / S)的接受程度越来越高,取决于它的长期有效性和在受污染场地的现场表现。早在1996年,就在英国希思罗机场附近的西德雷顿一个受污染的地点进行了S / S的深层土壤混合应用的现场试验。在两个月和4.5年的时间从​​该地点采集了岩心样品并进行了测试。与0.24年,2.4年和5年的土壤相比,本文研究了17年的受污染场地土壤的浸出特性。在土壤中使用了七种不同的水泥基粘合剂,包括水泥,PFA,石灰和膨润土,这些土壤被重金属和有机物的混合物所污染。两种浸出方法:毒性特征浸出程序(TCLP)和BS EN 12457用于研究稳定化/固化土壤中重金属的浸出行为。浸出试验结果表明,渗出液的pH值在开始的5年内随时间下降,然后在17年时趋于稳定。 BS EN 12457渗滤液的浓度低于饮用水标准,这表明S / S在使用17年后的性能令人满意。这些S / S土壤中重金属的浸出行为主要受粘合剂的碱度控制,其中一些重金属被硅酸钙水合物(C-S-H)凝胶相吸收。所施加的水泥基粘结剂内的粘结机理可以由它们的浸出液pH值决定,该浸出液pH值与它们相应的金属氢氧化物溶解度有关。

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