Institute of Geotechnical Engineering, School of Transportation, Southeast University, Nanjing, 210096, China.
Department of Earth and Atmospheric Sciences, University of Alberta, Edmonton, T6G 2E3, Canada.
Chemosphere. 2020 Jan;239:124738. doi: 10.1016/j.chemosphere.2019.124738. Epub 2019 Sep 5.
Stabilization/Solidification (S/S) has been widely used in soil remediation to both improve physical properties and immobilize extensive contaminants. GGBS (granulated ground blast furnace slag)-MgO-CaO (GMCs) was used to treat Pb/Zn contaminated soil. The physical and microstructural characteristics of stabilized/solidified contaminated soil were investigated in this study. Microstructural analysis showed that the main hydration products of GMC treated contaminated soil were C-S-H and hydrotalcite like gels (Ht), which dominated the physical strength of S/S soil. The unconfined compressive strength (UCS) and the leachability of GMC treated contaminated soil were improved with the increase in GMC proportion (5%-15%), curing time (7 days and 28 days) and temperature (5 °C, 21 °C and 45 °C) due to the enhanced hydration. The compressive strengths of the majority mixes met the US EPA criterion (0.35 MPa). The strength of S/S soils was less affected by the increase of curing temperature after a longer curing period (28 days). According to the XRD and SEM results, both Pb and Zn in S/S contaminated soil could be immobilized by the precipitation and the adsorption on the surface of calcium silicate hydrate (C-S-H). Zn can also be incorporated into the structure of C-S-H and Ht. The addition of Pb/Zn decreased the physical strength in the order of: Pb(5000 mg/kg)>Pb(10000 mg/kg)>Zn/Pb(5000 mg/kg)>Pb(20000 mg/kg).
稳定/固化 (S/S) 已广泛应用于土壤修复,以改善物理性质并固定大量污染物。矿渣微粉-氧化镁-氧化钙 (GMC) 被用于处理 Pb/Zn 污染土壤。本研究调查了稳定/固化污染土壤的物理和微观结构特性。微观结构分析表明,GMC 处理污染土壤的主要水化产物是 C-S-H 和类水滑石凝胶 (Ht),它们主导着 S/S 土壤的物理强度。随着 GMC 比例(5%-15%)、养护时间(7 天和 28 天)和温度(5°C、21°C 和 45°C)的增加,GMC 处理污染土壤的无侧限抗压强度 (UCS) 和浸出率得到提高,这是由于水化作用增强所致。大多数混合物的抗压强度符合美国环保署的标准(0.35 MPa)。在较长的养护期(28 天后),养护温度的升高对 S/S 土壤强度的影响较小。根据 XRD 和 SEM 结果,Pb 和 Zn 均可通过沉淀和在硅酸钙水合物 (C-S-H) 表面的吸附固定在 S/S 污染土壤中。Zn 也可以掺入 C-S-H 和 Ht 的结构中。Pb/Zn 的添加对物理强度的影响顺序为:Pb(5000 mg/kg) > Pb(10000 mg/kg) > Zn/Pb(5000 mg/kg) > Pb(20000 mg/kg)。