Textile Pollution Controlling Engineering Center of Ministry of Environmental Protection, College of Environmental Science and Engineering, Donghua University, Shanghai, People's Republic of China.
Environ Technol. 2023 Jun;44(15):2201-2214. doi: 10.1080/09593330.2021.2024888. Epub 2022 Feb 3.
Nowadays, polyhalogenated carbazoles (PHCZs) are a major pollutant that has recently sparked widespread concern. In this work, peroxymonosulfate (PMS) was activated by zero valent iron (Fe) to remove 3,6-dichlorocarbazole (3,6-CCZ). First, the key parameters influencing 3,6-CCZ degradation (PMS dosage, Fe dosage, initial pH, temperature and co-existing ions) were determined. Under the determined optimum conditions, the removal rate of 3,6-CCZ reached 100% within 1.5 h. Sulfate radicals (SO·), hydroxyl radicals (OH·), and singlet oxygen (O) generated in the reaction were directly identified with 0.1 M 5,5-dimethyl-1-pyrrolidine N-oxide (DMPO) by in-situ electron paramagnetic resonance (EPR) and indirectly identified by radical quenching experiments. The main reactive oxygen species (ROS) were different from most reported hydroxyl radicals (OH·) and sulfate radicals (SO·). In this study, it was found that OH· and O play a major role. Then, fresh and reacted Fe were characterized by XRD, SEM, and XPS. Iron corrosion products such as FeO, FeO, and FeOOH were generated. Finally, 3,6-CCZ degradation intermediates were identified by GC-MS and its degradation pathway was speculated. The intermediate pathway confirmed the combined action of (OH·) and (O) in 3,6-CCZ removal. This study provides new insight into the activation mechanism of Fe-activated PMS and the removal mechanism of 3,6-CCZ. Fe is a long-lasting and efficient catalyst of PMS for the degradation of 3,6-CCZ.The key parameters influencing 3,6-CCZ degradation were determined.The degradation pathways of 3,6-CCZ were inferred.OH· and O were the main ROS in Fe-activated PMS system.
如今,多卤代咔唑(PHCZs)是一种主要污染物,最近引起了广泛关注。在这项工作中,过一硫酸盐(PMS)通过零价铁(Fe)活化以去除 3,6-二氯咔唑(3,6-CCZ)。首先,确定了影响 3,6-CCZ 降解的关键参数(PMS 用量、Fe 用量、初始 pH 值、温度和共存离子)。在确定的最佳条件下,3,6-CCZ 在 1.5 h 内的去除率达到 100%。通过原位电子顺磁共振(EPR)直接用 0.1 M 5,5-二甲基-1-吡咯烷 N-氧化物(DMPO)鉴定反应中生成的硫酸根自由基(SO·)、羟基自由基(OH·)和单线态氧(O),并通过自由基猝灭实验间接鉴定。主要的活性氧物质(ROS)与大多数报道的羟基自由基(OH·)和硫酸根自由基(SO·)不同。在这项研究中,发现 OH·和 O 起主要作用。然后,通过 XRD、SEM 和 XPS 对新鲜和反应后的 Fe 进行了表征。生成了 FeO、FeO 和 FeOOH 等铁腐蚀产物。最后,通过 GC-MS 鉴定了 3,6-CCZ 降解中间产物,并推测了其降解途径。中间途径证实了(OH·)和(O)在 3,6-CCZ 去除中的协同作用。本研究为 Fe 活化 PMS 的活化机制和 3,6-CCZ 的去除机制提供了新的见解。Fe 是 PMS 降解 3,6-CCZ 的长效高效催化剂。确定了影响 3,6-CCZ 降解的关键参数。推断了 3,6-CCZ 的降解途径。OH·和 O 是 Fe 活化 PMS 体系中的主要 ROS。