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

机译:17岁的稳定/凝固污染污染污染地点的可浸出性

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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:增加了原位稳定/凝固(S / S)的接受取决于其污染地点的长期有效性和现场性能。 1996年在英国,在英国,在英国,S / S深土混合应用S / S深土混合应用的田间试验。核心样品在2个月和4.5岁处取自该网站并进行测试。本文与0.24,2.4和5年的性质相比,17年来解决污染部位土壤的浸出特性。使用七种不同的水泥基粘合剂,包括用重质金属和有机物鸡尾酒污染的土壤水泥,PFA,石灰和膨润土。两种浸出方法:应用毒性特征浸出程序(TCLP)和BS 12457,用于研究稳定/凝固土壤中重金属的浸出行为。浸出的试验结果表明,渗滤液pH随着时间的推移在前5年的时间下降,然后在17年内排水。 BS EN 12457渗滤液浓度低于饮用水标准,表明S / S在17年的服务时间的性能令人满意。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,其中一些重金属被吸收成硅酸钙水合物(C-S-H)凝胶相。所施加的水泥粘合剂内的结合机制可以通过它们与其相应的金属氢氧化溶解度相关的渗滤液pH来支配。

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