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用于重金属离子废物稳定化/固化的硬化矿渣浆体稳定性研究。

Investigation of the stability of hardened slag paste for the stabilization/solidification of wastes containing heavy metal ions.

作者信息

Rha C Y, Kang S K, Kim C E

机构信息

Department of Ceramic Engineering, Yonsei University, 134 Shinchon-dong, Seodaemoon-ku, Seoul, South Korea.

出版信息

J Hazard Mater. 2000 Apr 28;73(3):255-67. doi: 10.1016/s0304-3894(99)00185-5.

Abstract

We have studied the effect of chromium ions and lead ions on the chemical stability of hardened slag paste with toxic wastes during the stabilization/solidification process. The influences of Cr and Pb ions on the hydration of slag were also investigated. Sodium silicate (Na(2)SiO(3)), 5 wt.% of slag, was used as an alkali activator for slag hydration. The physical stability of hardened paste containing partial replacement of slag with fly ash and gypsum was also examined. When gypsum was added to slag, the compressive strength of hardened slag paste developed, accompanying the activation of alumino-ferrite-tricalciumsulfate (Al(2)O(3)-Fe(2)O(3)-3CaSO(4), AFt) and alumino-ferrite-monocalciumsulfate (Al(2)O(3)-Fe(2)O(3)-CaSO(4), AFm) phase generation. Those phases caused densification of the microstructure. Concurrently, the leaching amount of heavy metal ions was decreased. When fly ash was added to slag, the compressive strength increased and the leaching amount decreased with both active formation of aluminate hydrates and ion substitution. Lead ions were mostly stabilized through physical encapsulation by the hardened slag paste's hydrate matrix. In the case of chromium ions, we observed that it was mainly solidified through the formation of a substitutional solid solution with aluminum atoms in the structure of aluminate hydrates.

摘要

我们研究了铬离子和铅离子在稳定化/固化过程中对硬化矿渣浆体与有毒废物化学稳定性的影响。同时还研究了Cr和Pb离子对矿渣水化的影响。使用硅酸钠(Na₂SiO₃),占矿渣质量的5%,作为矿渣水化的碱激发剂。还考察了用粉煤灰和石膏部分替代矿渣的硬化浆体的物理稳定性。当向矿渣中添加石膏时,硬化矿渣浆体的抗压强度得到发展,同时伴随着铁铝酸钙三硫酸盐(Al₂O₃-Fe₂O₃-3CaSO₄,AFt)和铁铝酸钙单硫酸盐(Al₂O₃-Fe₂O₃-CaSO₄,AFm)相的生成。这些相导致微观结构致密化。同时,重金属离子的浸出量降低。当向矿渣中添加粉煤灰时,由于铝酸盐水合物的活性形成和离子替代,抗压强度增加且浸出量降低。铅离子主要通过硬化矿渣浆体的水合物基体的物理包裹作用而被稳定。对于铬离子,我们观察到它主要通过在铝酸盐水合物结构中与铝原子形成替代固溶体而被固化。

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