Department of Civil and Environmental Engineering, The Hong Kong Polytechnic University, Hung Hom, Kowloon, Hong Kong, China; Department of Materials Science and Engineering, The University of Sheffield, Sir Robert Hadfield Building, Mappin St, Sheffield S1 3JD, United Kingdom.
Department of Civil and Environmental Engineering, The Hong Kong Polytechnic University, Hung Hom, Kowloon, Hong Kong, China; Geological Environment Division, Korea Institute of Geoscience and Mineral Resources, Gwahak-ro 124, Yuseong-gu, Daejeon 34132, Republic of Korea.
Environ Int. 2019 May;126:336-345. doi: 10.1016/j.envint.2019.02.057. Epub 2019 Feb 28.
Stabilization/solidification (S/S) is a low-cost and high-efficiency remediation method for contaminated soils, however, conventional cement-based S/S method has environmental constraints and sustainability concerns. This study proposes a low-carbon, cement-free, clay-based approach for simultaneous S/S of As and Pb in the contaminated soil, and accordingly elucidates the chemical interactions between alkali-activated clay binders and potentially toxic elements. Quantitative X-ray diffraction and Al nuclear magnetic resonance analyses indicated that the addition of lime effectively activated the hydration of kaolinite clay, and the presence of limestone further enhanced the polymerization of hydrates. X-ray photoelectron spectroscopy showed that approximately 19% of As was oxidized to As in the alkali-activated clay system, which reduced toxicity and facilitated immobilization of As. During the cement-free S/S process, As and Pb consumed Ca(OH) and precipitated as Ca(AsO)·4HO and Pb(NO)(OH), respectively, accounting for the low leachability of As (7.0%) and Pb (5.4%). However, the reduced amount of Ca(OH) decreased the degree of hydration of clay minerals, and the pH buffering capacity of the contaminated soil hindered the pH increase. Sufficient dosage of lime was required for ensuring satisfactory solidification and contaminant immobilization of the clay-based S/S products. The leachability of As and Pb in high-Ca S/S treated soil samples was reduced by 96.2% and 98.8%, respectively. This is the first study developing a green and cement-free S/S of As- and Pb-contaminated soil using clay minerals as an environmentally compatible binding material.
稳定化/固化(S/S)是一种低成本、高效率的污染土壤修复方法,然而,传统的基于水泥的 S/S 方法存在环境限制和可持续性问题。本研究提出了一种低碳、无水泥、基于粘土的方法,用于同时 S/S 污染土壤中的 As 和 Pb,并相应阐明了碱激活粘土粘结剂与潜在有毒元素之间的化学相互作用。定量 X 射线衍射和 Al 核磁共振分析表明,石灰的添加有效地激活了高岭石粘土的水化,而石灰石的存在进一步增强了水合物的聚合。X 射线光电子能谱表明,在碱激活粘土体系中,约 19%的 As 被氧化为 As,从而降低了 As 的毒性并促进了 As 的固定。在无水泥 S/S 过程中,As 和 Pb 消耗了 Ca(OH)并分别沉淀为 Ca(AsO)·4HO 和 Pb(NO)(OH),这导致 As 的浸出率(7.0%)和 Pb 的浸出率(5.4%)较低。然而,Ca(OH)的减少量降低了粘土矿物的水合程度,并且污染土壤的 pH 缓冲能力阻碍了 pH 的增加。需要足够剂量的石灰以确保基于粘土的 S/S 产品对污染土壤的固化和污染物固定达到令人满意的效果。高钙 S/S 处理的土壤样品中 As 和 Pb 的浸出率分别降低了 96.2%和 98.8%。这是首次使用粘土矿物作为环境相容的粘结材料,开发出一种绿色、无水泥的 S/S 处理含 As 和 Pb 污染土壤的方法。