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Immobilization of mercury and zinc in an alkali-activated slag matrix

机译:将汞和锌固定在碱活化炉渣基质中

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The behavior of heavy metals mercury and zinc immobilized in an alkali-activated slag (AAS) matrix has been evaluated using physical property tests, pore structure analysis and XRD, TG-DTG, FTIR and TCLP analysis. Low concentrations (0.5%) of mercury and zinc ions had only a slight affect on compressive strength, pore structure andhydration of AAS matrixes. The addition of 2% Hg ions to the AAS matrix resulted in a reduction in early compressive strength but no negative effects were noticed after 28 days of hydration. Meanwhile, 2% Hg ions can be effectively immobilized in the AAS matrix with the leachate meeting the USEPA TCLP mercury limit. For a 2% Zn-doped AAS matrix, the hydration of the AAS paste was greatly retarded and the zinc concentration in the leachate from this matrix was higher than 5 mg/l even at 28 days. Based on these results, we conclude that the physical encapsulation and chemical fixation mechanisms were likely to be responsible for the immobilization of Hg ions in the AAS matrix while only chemical fixation mechanisms were responsible for the immobilization of Zn ions in the AAS matrix.
机译:使用物理性能测试,孔结构分析以及XRD,TG-DTG,FTIR和TCLP分析,评估了固定在碱活化矿渣(AAS)基质中的重金属汞和锌的行为。低浓度(0.5%)的汞和锌离子对AAS基质的抗压强度,孔结构和水合影响很小。在AAS基质中添加2%的Hg离子会导致早期抗压强度降低,但在水合28天后未发现负面影响。同时,可以将2%的Hg离子有效地固定在AAS基质中,且沥出液达到USEPA TCLP汞限值。对于掺杂2%Zn的AAS基体,即使在28天时,AAS浆料的水化作用也大大受阻,并且来自该基体的渗滤液中的锌浓度仍高于5 mg / l。基于这些结果,我们得出结论,物理包封和化学固定机制很可能是将汞离子固定在AAS基质中的原因,而只有化学固定机制才将Zn离子固定在AAS基质中。

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