Guangdong Key Laboratory of Environmental Catalysis and Health Risk Control, School of Environmental Science and Engineering, Institute of Environmental Health and Pollution Control, Guangdong University of Technology, Guangzhou 510006, China.
Guangdong Key Laboratory of Environmental Catalysis and Health Risk Control, School of Environmental Science and Engineering, Institute of Environmental Health and Pollution Control, Guangdong University of Technology, Guangzhou 510006, China.
J Hazard Mater. 2020 Nov 5;398:122826. doi: 10.1016/j.jhazmat.2020.122826. Epub 2020 May 20.
In this study, polycyclic aromatic hydrocarbons (PAHs) at practical concentrations in the simulated sludge treated by the Fe/HO and Fe/peroxymonosulfate (PMS) systems were evaluated in terms of the PAHs (phenanthrene, anthracene, fluoranthene) removal, element migration, Cl effect, and chlorination by-product formation. The results indicated that according to the removal rate of PAHs, the optimal dosage of the Fe/PMS system (∑PAHs removal rate was 64.66 ± 2.82 %) was 1/30 of that for the Fe/HO system (∑PAHs removal rate was 78.63 ± 0.38 %). The elemental contents in the simulated sludge were mainly affected by the extent of advanced oxidation and the amount of generated iron flocs. By studying the PAHs removal, free chlorine formation, total organochlorine content, and PAHs products in Fe/HO/Cl and Fe/PMS/Cl systems, it was found that chlorine radicals (·Cl) had high reactivity with phenanthrene and fluoranthene, whereas dichloride anion radicals (Cl) exhibited the opposite behavior. Furthermore, PAHs were oxidized by ·Cl and hydroxyl radical in the Fe/HO/Cl system, whereas PAHs and their products were chlorinated by free chlorine and ·Cl in the Fe/PMS/Cl system to six chlorinated by-products such as Cl-PAHs (9-Cl-phenanthrene, 2-Cl-anthracene, 9,10-Cl-anthracene, 3-Cl-fluoranthene). These results provide some useful suggestions for the safe advanced oxidation process treatment of textile dyeing sludge.
在本研究中,评估了实际浓度的多环芳烃(PAHs)在 Fe/HO 和 Fe/过一硫酸盐(PMS)系统处理的模拟污泥中的去除效果、元素迁移、Cl 效应以及氯化副产物形成。结果表明,根据 PAHs 的去除率,Fe/PMS 系统的最佳剂量(∑PAHs 去除率为 64.66±2.82%)是 Fe/HO 系统的 1/30(∑PAHs 去除率为 78.63±0.38%)。模拟污泥中的元素含量主要受高级氧化程度和生成的铁絮体数量的影响。通过研究 Fe/HO/Cl 和 Fe/PMS/Cl 系统中 PAHs 的去除、自由氯生成、总有机氯含量和 PAHs 产物,发现氯自由基(·Cl)与菲和荧蒽具有高反应活性,而二氯阴离子自由基(Cl)则表现出相反的行为。此外,PAHs 在 Fe/HO/Cl 系统中被·Cl 和羟基自由基氧化,而在 Fe/PMS/Cl 系统中,PAHs 和其产物被自由氯和·Cl 氯化生成六个氯化副产物,如 Cl-PAHs(9-Cl-菲、2-Cl-蒽、9,10-Cl-蒽、3-Cl-荧蒽)。这些结果为纺织染料污泥的安全高级氧化处理提供了一些有用的建议。