Modulating the redox couples of graphene-like NBC-TiO2@FeMn through forming photo-Fenton system for boosting persulfate activation to accelerate the contaminant degradation

氧化还原 过硫酸盐 激进的 电子转移 化学 光化学 石墨烯 降级(电信) 催化作用 羟基自由基 半反应 无机化学 化学工程 材料科学 纳米技术 有机化学 工程类 电信 计算机科学
作者
He Bai,Yuxiang Yang,Jining Zhang,Yubing Yang,Hongming Yuan,Mengyang Dong,Chengyin Wang,Chaoying Ni
出处
期刊:Chemical Engineering Journal [Elsevier]
卷期号:473: 145392-145392 被引量:3
标识
DOI:10.1016/j.cej.2023.145392
摘要

The sluggish cycling of redox couples hampers the practical application of catalysts in contaminant degradation. Herein, a novel strategy was introduced by constructing a photo-Fenton system onto the graphene-like NBC to realize the ultrafast modulating of redox couples during the contaminant degradation. The constructed NBC-TiO2@FeMn (NBTF) exhibits a higher proportion of reductive redox couples (Fe (II)/Mn (II)) after the degradation, which is attributable to the photo-Fenton system and the graphene-like NBC with high electron transfer efficiency. Density functional theory (DFT) calculations also confirm that constructing the photo-Fenton system on graphene-like NBC greatly enhances electron transfer, enabling the modulation of redox couples during the degradation process. During activation, various reactive oxygen species (including •OH, SO4•-, high-valent metal oxides, and non-radical pathways) are generated, effectively degrading pulp wastewater Tetrachloroguaiacol (TeCG) with a degradation efficiency of 98.8 % within 14 min. Quenching experiments and EPR spectroscopic analysis indicate that the degradation of TeCG is mainly mediated by hydroxyl radicals (•OH) and sulfate radicals (SO4•-) as predominant pathways, while high-valent metal oxides, 1O2 and direct electron transfer mechanisms act in a cooperative manner. Substitution reaction on active sites reveal that both FeMn LDH and graphene-like NBC are identified as the main active sites, with Mn exhibiting superior PMS activation compared to Fe. A possible degradation pathway of TeCG is proposed, and a decrease in the toxicity of intermediates is observed. This study provides a new perspective on the modulation of redox couples in SR-AOPs to realize sustainable pollutants degradation.
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