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在不同养护温度下,固化/稳定化 Pb/Zn 污染土壤的 GMCs:物理和微观结构性能。

GMCs stabilized/solidified Pb/Zn contaminated soil under different curing temperature: Physical and microstructural properties.

机构信息

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.

出版信息

Chemosphere. 2020 Jan;239:124738. doi: 10.1016/j.chemosphere.2019.124738. Epub 2019 Sep 5.

Abstract

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).

摘要

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)。

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