详细信息
Application of sulfidated nano zero-valent iron to enhance fluoranthene degradation by Fe(III) activated sodium percarbonate process in aqueous and soil media ( SCI-EXPANDED收录 EI收录)
文献类型:期刊文献
英文题名:Application of sulfidated nano zero-valent iron to enhance fluoranthene degradation by Fe(III) activated sodium percarbonate process in aqueous and soil media
作者:Sheng, Xianxian[1];Liu, Yulong[1];Ali, Meesam[2];Habib, Mudassir[1];Fu, Rongbing[3];Lyu, Shuguang[1]
机构:[1]East China Univ Sci & Technol, State Environm Protect Key Lab Environm Risk Asses, Shanghai 200237, Peoples R China;[2]Muhammad Nawaz Sharif Univ Engn & Technol, Dept Chem Engn, Multan 60000, Pakistan;[3]Tongji Univ, Ctr Environm Risk Management & Remediat Soil & Gro, State Key Lab Pollut Control & Resource Reuse, Shanghai 200092, Peoples R China
年份:2024
卷号:12
期号:3
外文期刊名:JOURNAL OF ENVIRONMENTAL CHEMICAL ENGINEERING
收录:;EI(收录号:20242016099602);WOS:【SCI-EXPANDED(收录号:WOS:001242902400001)】;
基金:This study was financially supported by the National Key R & D Pro- gram of China (No. 2023YFC3707700) .
语种:英文
外文关键词:Sulfidated nano zero-valent iron; Fluoranthene; Sodium percarbonate; Soil and groundwater
摘要:Iron sludge generation poses a challenge to the application of Fenton/Fenton-like processes in wastewater treatment. In this study, sulfidated nano zero-valent iron (S-nZVI) was introduced to enhance the activation of sodium percarbonate (SPC) by Fe(III), mitigating the generation of iron sludge by promoting the Fe(III)/Fe(II) cycle. The proposed technique efficiently removed 94.3 % fluoranthene (FLT) in which HO center dot acted as the major reactive oxygen species responsible for FLT degradation. Toxicity analysis revealed phthalic acid and 1-phenylnaphthalene as FLT degradation intermediates which finally converted to CO2 and H2O. Similarly, the luminous bacteria experiment also showed that the FLT degradation process was environmentally benign. The support of SnZVI to the Fe(III)/Fe(II) cycle was determined by analyzing the morphology and characterization of S-nZVI. The removal of FLT reached more than 80 % at pH ranging from 3.0 to 10.0, and the detrimental effects of low concentrations of Cl- were mitigated. SPC/S-nZVI/Fe(III) process showed good removal of FLT (90 %) in both real groundwater and river simulation experiments. Furthermore, SPC/S-nZVI/Fe(III) process was successfully applied in soil slurry media with around 90 % FLT degradation in 12 h. The influence of the soil/water ratio on FLT removal was found to be negligible. SPC/S-nZVI/Fe(III) process was superior for the removal of mixed FLT, naphthalene, and phenanthrene contamination. In conclusion, the SPC/S-nZVI/Fe(III) system exhibits enormous potential in the remediation of polycyclic aromatic hydrocarbons (PAHs) contaminated sites.
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