Key Laboratory of Ministry of Education on Pollution Control and Ecosystem Restoration in Industry Clusters, Guangdong Provincial Key Laboratory of Solid Wastes Pollution Control and Recycling, School of Environment and Energy, South China University of Technology, Guangzhou 510006, Guangdong, China.
Key Laboratory of Ministry of Education on Pollution Control and Ecosystem Restoration in Industry Clusters, Guangdong Provincial Key Laboratory of Solid Wastes Pollution Control and Recycling, School of Environment and Energy, South China University of Technology, Guangzhou 510006, Guangdong, China.
J Hazard Mater. 2021 Jul 15;414:125555. doi: 10.1016/j.jhazmat.2021.125555. Epub 2021 Mar 2.
Sulfurized nanoscale zerovalent iron (S-nZVI) has been widely reported to be able to quickly remove heavy metals/persistent organic pollutants, but the limited understanding of the complicated removal process of heavy metals-organic combined pollutants restricts the application of S-nZVI. Here, we demonstrate that there is significant difference in the effectiveness of S-nZVI for removing single pollutant and complex pollutants. The removal kinetic constant (k) of heavy metals by S-nZVI followed a sequence of Cr(VI)>Pb(II)>Ni(II)>Cd(II) with or without polybrominated diphenyl ethers (PBDEs). While the capacity of co-existing cations increasing the k of PBDEs followed the order: Ni(II)>Pb(II)>Cd(II), and the co-existence of Cr(VI) anion inhibited the reduction of PBDE by S-nZVI because the generated Cr-Fe precipitate hindered the electron transfer. The de-passivation process on S-nZVI surface by Cd(II) ions slightly accelerated the transformation rate of electron. Nevertheless, the co-existing Pb(II) significantly accelerated the transformation of BDE-209 via the galvanic effect from the generated Pb/Fe bimetal. Interestingly, the k of BDE-47 in Ni(II)/S-nZVI system was 5.51 times higher than that of Pb(II)/S-nZVI system, implying that an atomic hydrogen mechanism dominated the reduction of BDE-47 by Ni(II)/S-nZVI. In conclusion, the results provided a deep comprehending of removal mechanism of heavy metal-organic complex pollutants by S-nZVI.
硫化纳米零价铁(S-nZVI)已被广泛报道能够快速去除重金属/持久性有机污染物,但由于对重金属-有机复合污染物复杂去除过程的认识有限,限制了 S-nZVI 的应用。在这里,我们证明了 S-nZVI 去除单一污染物和复杂污染物的效果有显著差异。S-nZVI 去除重金属的动力学常数(k)遵循 Cr(VI)>Pb(II)>Ni(II)>Cd(II)的顺序,无论是否存在多溴联苯醚(PBDEs)。而共存阳离子增加 PBDEs 的 k 的能力顺序为:Ni(II)>Pb(II)>Cd(II),Cr(VI)阴离子的共存抑制了 S-nZVI 对 PBDE 的还原,因为生成的 Cr-Fe 沉淀物阻碍了电子转移。Cd(II)离子对 S-nZVI 表面的去钝化过程略微加速了电子的转化速率。然而,共存的 Pb(II)通过生成的 Pb/Fe 双金属显著加速了 BDE-209 的转化。有趣的是,Ni(II)/S-nZVI 体系中 BDE-47 的 k 比 Pb(II)/S-nZVI 体系高 5.51 倍,这意味着原子氢机制主导了 Ni(II)/S-nZVI 对 BDE-47 的还原。总之,结果提供了对 S-nZVI 去除重金属-有机复合污染物的去除机制的深入理解。