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Ascorbic acid enhanced the circulation between Fe(II) and Fe(III) in peroxymonosulfate system for fluoranthene degradation

Journal 2024 · IF 2.5 · 89(7): 1682-1700 · 发表于 2024 年 3 月 26 日
作者: Zhang Longbin,Gao Jianxiong,Liu Yulong,Zhou Zhengyuan,Sheng Xianxian,Li Dexiao,Chen Yuantian,Lyu Shuguang
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摘要

View large Download slide View large Download slide Close modal In this research, ascorbic acid (AA) was used to enhance Fe(II)/Fe(III)-activated permonosulfate (PMS) systems for the degradation of fluoranthene (FLT). AA enhanced the production of ROS in both PMS/Fe(II) and PMS/Fe(III) systems through chelation and reduction and thus improved the degradation performance of FLT. The optimal molar ratio in PMS/Fe(II)/AA/FLT and PMS/Fe(III)/AA/FLT processes were 2/2/4/1 and 5/10/5/1, respectively. In addition, the experimental results on the effect of FLT degradation under different groundwater matrixes indicated that PMS/Fe(III)/AA system was more adaptable to different water quality conditions than the PMS/Fe(II)/AA system. was the major reactive oxygen species (ROS) responsible for FLT removal through the probe and scavenging tests in both systems. Furthermore, the degradation intermediates of FLT were analyzed using gas chromatograph-mass spectrometry (GC-MS), and the probable degradation pathways of FLT degradation were proposed. In addition, the removal of FLT was also tested in actual groundwater and the results showed that by increasing the dose and pre-adjusting the solution pH, 88.8 and 100% of the FLT was removed for PMS/Fe(II)/AA and PMS/Fe(III)/AA systems. The above experimental results demonstrated that PMS/Fe(II)/AA and PMS/Fe(III)/AA processes have a great perspective in practice for the rehabilitation of FLT-polluted groundwater. The effect of AA on the circulation between Fe(II) and Fe(III) in the PMS system was investigated. SO 4 •− was the primary ROS in PMS/Fe(II)/AA and PMS/Fe(III)/AA systems. The effect of actual groundwater matrixes on FLT removal was investigated. The possible degradation pathways of FLT were proposed. Effective degradation of FLT in actual groundwater was achieved.

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