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由 CN 的 N 空位锚定的单个 Fe 原子激活过一硫酸盐以有效降解难降解有机物:通过 O 和 Fe(IV)=O 的非自由基途径的关键作用。

Single Fe atom anchored by N vacancy of CN activates PMS for efficient degradation of refractory organics: The key role of non-radical pathway through O and Fe(IV)=O.

作者信息

Tu Shenghui, Sun Lu, Zhang Hongxiang, Xie Jiaqi, Shen Leizhen, Liu Wenming, Li Guobo, Peng Honggen

机构信息

School of Chemistry and Chemical Engineering, Key Laboratory of Jiangxi Province for Environment and Energy Catalysis, Nanchang University, Nanchang 330031, China.

School of Resources and Environment, Key Laboratory of Poyang Lake Environment and Resource Utilization, Ministry of Education, Nanchang University, Nanchang 330031, China.

出版信息

J Environ Sci (China). 2026 Jan;159:339-348. doi: 10.1016/j.jes.2025.03.039. Epub 2025 Mar 31.

DOI:10.1016/j.jes.2025.03.039
PMID:41005891
Abstract

Fenton-like technology based on peroxymonosulfate activation has shown great potential in refractory organics degradation. In this work, single Fe atom catalysts were synthesized through facile ball milling and exhibited very high performance in peroxymonosulfate activation. The Fe single-atom filled an N vacancy on the triazine ring edge of CN, as confirmed through X-ray absorption fine structure, density functional calculation and electron paramagnetic resonance. The SAFeCN/PMS system could completely remove phenol (20 mg/L) within 10 min and its first-order kinetic constant was 12.3 times that of the FeO/PMS system. Under different initial pH levels and in various anionic environments, SAFeCN still demonstrated excellent catalytic activity, achieving a removal rate of over 90 % for phenol within 12 min. In addition, SAFeCN exhibited outstanding selectivity in reaction systems with different pollutants, showing excellent degradation effects on electron-rich pollutants only. Hydroxyl radicals (OH), singlet oxygen (O) and high-valent iron oxide (Fe(Ⅳ)=O) were detected in the SAFeCN/PMS system through free radical capture experiments. Further experiments on the quenching of active species and a methyl phenyl sulfoxide probe confirmed that O and Fe(Ⅳ)=O played dominant roles. Additionally, the change in the current response after adding PMS and phenol in succession proved that a direct electron transfer path between organic matter and the catalyst surface was unlikely to exist in the SAFeCN/PMS/Phenol degradation system. This study provides a new demonstration of the catalytic mechanism of single-atom catalysts.

摘要

基于过一硫酸盐活化的类芬顿技术在难降解有机物降解方面展现出巨大潜力。在本工作中,通过简便的球磨法合成了单原子铁催化剂,其在过一硫酸盐活化方面表现出非常高的性能。通过X射线吸收精细结构、密度泛函计算和电子顺磁共振证实,铁单原子填充在CN三嗪环边缘的N空位上。SAFeCN/PMS体系能在10分钟内完全去除苯酚(20mg/L),其一级动力学常数是FeO/PMS体系的12.3倍。在不同初始pH值和各种阴离子环境下,SAFeCN仍表现出优异的催化活性,在12分钟内对苯酚的去除率达到90%以上。此外,SAFeCN在含有不同污染物的反应体系中表现出出色的选择性,仅对富电子污染物显示出优异的降解效果。通过自由基捕获实验在SAFeCN/PMS体系中检测到了羟基自由基(OH)、单线态氧(O)和高价铁氧化物(Fe(Ⅳ)=O)。进一步的活性物种猝灭实验和甲基苯基亚砜探针实验证实,O和Fe(Ⅳ)=O起主要作用。此外,连续加入PMS和苯酚后电流响应的变化证明,在SAFeCN/PMS/苯酚降解体系中,有机物与催化剂表面之间不太可能存在直接电子转移路径。本研究为单原子催化剂的催化机理提供了新的例证。

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