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Experimental Investigation of Cement/Soda Residue for Solidification/Stabilization of Cr-Contaminated Soils

机译:CR污染土壤凝固/稳定化水泥/苏打残余物的实验研究

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Adopting more efficient and sustainable remediation materials is of great importance for the development of solidification and stabilization (S/S) technology. Among them, soda residue could be considered as a desirable binder due to its strong adsorption for heavy metals. For understanding of the performance of Cr-contaminated soils treated by cement/soda residue, the strength, leaching and microstructural characteristics, and the long-term effectiveness under wetting-drying cycles were comprehensively investigated in this study. The results showed that the unconfined compressive strength (UCS) increased and the leached Cr3+ concentration decreased with curing time, binder content, and binder ratio. Increasing the soda residue from C6S14 to C6S24 could improve soil strength and reduce leachability of Cr3+, while a reverse trend was presented with increasing initial Cr3+ concentration. With subsequent wetting-drying cycles, the UCS further increased and then decreased; inversely, the leached Cr3+ decreased, followed by an increase of Cr-contaminated soils. For the specimens of C6S14 and C6S24, the maximum UCS of 6.04?MPa and 6.48?MPa was reached; correspondingly, the minimum leached Cr3+ concentration of 2.78?mg/L and 1.93?mg/L was reached after 3 wetting-drying cycles, respectively. Microstructure analysis results found that reaction products like calcium silicate hydrate (C-S-H) and ettringite (AFt) increasingly occupied the soil pore space and caused a denser soil structure after 3 wetting-drying cycles, which indicated the long-term effectiveness of contaminated soils treated by cement/soda residue.
机译:采用更高效和可持续的修复材料对于凝固和稳定(S / S)技术的发展是重要的。其中,由于其对重金属的强烈吸附,苏打残余物可以被认为是理想的粘合剂。为了了解通过水泥/苏打残余物处理的Cr污染土壤的性能,在本研究中全面研究了润湿干燥循环的强度,浸出和微观结构特征和润湿干燥循环的长期效果。结果表明,不束缚的压缩强度(UCS)增加,浸出的CR3 +浓度随固化时间,粘合剂含量和粘合剂比率降低。将来自C6S14至C6S24的钠残基增加可以提高土壤强度并降低Cr3 +的可浸出性,而初始Cr3 +浓度的增加提出了反向趋势。随后润湿干燥循环,UCS进一步增加然后减少;相反,浸出的CR3 +降低,然后增加了Cr污染的土壤。对于C6S14和C6S24的标本,最大UC为6.04?MPa和6.48?MPa;相应地,在3个润湿干燥循环后,分别达到最小浸出的Cr3 +浓度为2.78×mg / L和1.93?Mg / L.微观结构分析结果发现,硅酸钙水合物(CSH)和Ettringite(AFT)等反应产物越来越多地占据了土壤孔隙空间,并在3次润湿干燥循环后引起了更密集的土壤结构,这表明污染的土壤治疗的长期有效性水泥/苏打残留物。

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