Abstract
The solidification/stabilization mechanism of each cementious material was investigated. It was found that when $C_3$S was hydrated , the Pb element could be transferred to the insoluble Ca[Pb(OH)$_3$.$H_2O$]$_2$and the Cr element to the CaCr $O_4$$H_2O$. The addition of heavy metal tends to delay the hydration until initial 7 days. The Pb element as also delayed the hydration and the Cr element was substituted for the ettringite. On the occasion of the hydration of $C_4$ $A_3$ $S^{S}$, the Pb and Cr ions were solidified/stabilized by the substitution into the ettringite and/or monosulfate. Leaching of the Pb, Cr and Zn elements in the solidified material was extremely little, indicating that heavy metals were effectively solidified/stabilized in the hydrated cementious materials. Solidification/stabilization of heavy metal ions in the industrial wastes such as the STS, BF and COREX sludge was investigated. In case of the mixing ratio of cement and slag was 3 : 7, leaching of hazardous heavy metal ions was very little, indications that the solidification and stabilization was very successful.l.
각 시멘트 구성 광물별로 중금속의 고정/안정화 메커니즘과 수화거동을 검토하였다. $C_3$S수화 시 Pb는 불용성화합물인 Ca[Pb(OH)$_3$.$H_2O$]$_2$를, Cr은 CaCr $O_4$$H_2O$를 생성하였으며, 초기 7일까지는 전체적으로 중금속이 첨가되어진 경우 수화가 늦어지는 경향을 보이고 있었다. $C_3$A와 $C_4$ $A_3$ $S^{S}$수화 시 Pb, Cr 이온이 ettringite 또는 monosulfate에 의한 수화물에 치환에 의한 고정/안정화되고 있다. 수화물에서 Pb, Cr, Zn등 유해중금속의 용출은 극미하였으며 이는 수화물에 중금속이 고정/안정화되었음을 알 수 있다. 슬래그 혼합 시멘트를 이용한 산업 폐기물 STS, BF, COREX 슬러지 함유 중금속의 고정화/안정화를 검토하였다 시멘트와 폐슬러지를 3 : 7의 비율로 혼합 고화 처리한 결과 유해 중금속의 용출은 극미하였으며, 효과적으로 고정/안정화됨을 확인할 수 있었다.다.
