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Heavy metal leaching and distribution in glass products from the co-melting treatment of electroplating sludge and MSWI fly ash

机译:电镀污泥和MSWI粉煤灰的共熔处理在玻璃产品中的重金属浸出和分布

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摘要

Melting is a common solidification treatment that concentrates and encapsulates heavy metals into a glass matrix for waste containing heavy metals (Chae et al., 2016). To control the risk of heavy metal leaching into the glass product, a reduction in the amount of heavy metal was achieved in a pilot-scale furnace by co-melting electroplating sludge (EPS) and municipal solid waste incineration fly ash (MSWI FA). Through the melting process, the chloride from MSWI FA led to heavy metals volatilization in the form of chlorine salts. The fly ash additionally increased heavy metals volatilization by 4%-91%. The highest volatilization ratios of Zn, Pb, Cu, Cd, Cr and Ni were 33%, 96%, 33%, 79%, 81% and 31%, respectively. The concentrations of Pb and Zn in the secondary fly ash were close to the Pb and Zn concentrations in lead-zinc ore that are required in smelting industry. Moreover, glass sand was produced after the melting treatment. With an increase in the fly ash mixing ratio, the leaching concentration of Zn and Cu decreased to 3.8 mg/L and 2.1 mg/L. The leaching concentrations of other heavy metals stayed below 1 mg/L in all cases. When the ratio of MSWI FA reached 10%, the glass sand contained the least amount of impurities and a large amount of phosphate and silicate, which were probably responsible for the stability of the heavy metals. Therefore, our results provided a promising approach to the stability of the waste by the recovery of heavy metals in the co-treatment of heavy metal-bearing wastes.
机译:熔化是一种常见的固化处理方法,它将重金属浓缩并封装到玻璃基质中,以处理含重金属的废物(Chae等人,2016)。为了控制重金属浸入玻璃产品的风险,通过将电镀污泥(EPS)和城市固体废物焚烧飞灰(MSWI FA)混合熔融,在中试炉中减少了重金属的含量。通过熔融过程,MSWI FA中的氯化物导致氯盐形式的重金属挥发。粉煤灰还使重金属的挥发增加了4%-91%。 Zn,Pb,Cu,Cd,Cr和Ni的最高挥发比分别为33%,96%,33%,79%,81%和31%。二次粉煤灰中的Pb和Zn的浓度接近冶炼行业所需的铅锌矿石中的Pb和Zn的浓度。此外,在熔融处理之后产生玻璃砂。随着粉煤灰混合比的增加,锌和铜的浸出浓度分别降至3.8 mg / L和2.1 mg / L。在所有情况下,其他重金属的浸出浓度均保持在1 mg / L以下。当MSWI FA的比例达到10%时,玻璃砂中的杂质最少,而磷酸盐和硅酸盐则很多,这可能是重金属稳定性的原因。因此,我们的结果为在含重金属废物的协同处理中通过回收重金属提供了一种有前途的方法来稳定废物。

著录项

  • 来源
    《Journal of Environmental Management》 |2019年第15期|226-235|共10页
  • 作者单位

    Shanghai Univ, Sch Environm & Chem Engn, 99 Shangda Rd, Shanghai 200444, Peoples R China;

    Shanghai Univ, Sch Environm & Chem Engn, 99 Shangda Rd, Shanghai 200444, Peoples R China;

    Zhejiang Environm Sci & Design Inst, 109 Tianmushan Rd, Hangzhou 310000, Zhejiang, Peoples R China;

    Shanghai Univ, Sch Environm & Chem Engn, 99 Shangda Rd, Shanghai 200444, Peoples R China;

    Shanghai Univ, Sch Environm & Chem Engn, 99 Shangda Rd, Shanghai 200444, Peoples R China;

    Shanghai Univ, Sch Environm & Chem Engn, 99 Shangda Rd, Shanghai 200444, Peoples R China;

    Shanghai Univ, Sch Environm & Chem Engn, 99 Shangda Rd, Shanghai 200444, Peoples R China;

  • 收录信息 美国《科学引文索引》(SCI);美国《化学文摘》(CA);
  • 原文格式 PDF
  • 正文语种 eng
  • 中图分类
  • 关键词

    Electroplating sludge; MSWI fly ash; Co-melting; Heavy metals; Vitrification;

    机译:电镀污泥;MSWI粉煤灰;共熔;重金属;玻璃化;

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