{"title":"Enhanced chlorine activation on Cu-doped goethite via the synergistic effect of Cu+ and oxygen vacancy for efficient organic pollutant degradation","authors":"Ziyi Liu, Jun Hao, Xiufang Zhang, Guanlong Wang","doi":"10.1016/j.esi.2025.12.003","DOIUrl":null,"url":null,"abstract":"<div><div>The goethite (FeOOH) has become a cost-effective and efficient alternative for triggering chlorine-based advanced oxidation technology towards water purification. However, the performance of FeOOH was limited by the sluggish Fe<sup>3+</sup>/Fe<sup>2+</sup> cycling. Herein, the Cu doped FeOOH (Cu-FeOOH) catalysts with varying Cu doping levels were designed and synthesized, aiming to enhance the chlorine activation efficiency of FeOOH for efficient organic pollutants removal. The results indicated that the Cu doping significantly enhanced catalytic activity of FeOOH, and the Cu-FeOOH with moderate Cu doping level (15-Cu-FeOOH) performed best. The 15-Cu-FeOOH enabled almost complete removal of atrazine within 30 min, whose reaction rate (0.18 min<sup>−1</sup>) was 233.6 times higher than that of pristine FeOOH (7.8 ×10<sup>−4</sup> min<sup>−1</sup>). Additionally, 15-Cu-FeOOH/chlorine system demonstrated universal performance towards diverse organic pollutants, extremely low metal leaching and satisfactory cyclic performance. Quenching and probe experiments elucidated •OH primarily contributed to pollutant degradation, while •Cl and •ClO played subordinate roles. Mechanistic insights revealed that the incorporated Cu<sup>+</sup> and oxygen vacancy (O<sub>v</sub>) synergistically enhanced performance of Cu-FeOOH: Cu<sup>+</sup> enabled efficient Fe<sup>3+</sup>/Fe<sup>2+</sup> cycling via formed Cu-O-Fe bond while O<sub>v</sub> expedited Cu<sup>2+</sup>/Cu<sup>+</sup> cycling through Cu-O<sub>v</sub> interaction for Cu<sup>+</sup> recovery, thus resulting in sustained chlorine activation to produce powerful reactive species for pollutant degradation.</div></div>","PeriodicalId":100486,"journal":{"name":"Environmental Surfaces and Interfaces","volume":"4 ","pages":"Pages 18-27"},"PeriodicalIF":0.0000,"publicationDate":"2026-12-01","publicationTypes":"Journal Article","fieldsOfStudy":null,"isOpenAccess":false,"openAccessPdf":"","citationCount":"0","resultStr":null,"platform":"Semanticscholar","paperid":null,"PeriodicalName":"Environmental Surfaces and Interfaces","FirstCategoryId":"1085","ListUrlMain":"https://www.sciencedirect.com/science/article/pii/S2949864325000347","RegionNum":0,"RegionCategory":null,"ArticlePicture":[],"TitleCN":null,"AbstractTextCN":null,"PMCID":null,"EPubDate":"2025/12/10 0:00:00","PubModel":"Epub","JCR":"","JCRName":"","Score":null,"Total":0}
引用次数: 0
Abstract
The goethite (FeOOH) has become a cost-effective and efficient alternative for triggering chlorine-based advanced oxidation technology towards water purification. However, the performance of FeOOH was limited by the sluggish Fe3+/Fe2+ cycling. Herein, the Cu doped FeOOH (Cu-FeOOH) catalysts with varying Cu doping levels were designed and synthesized, aiming to enhance the chlorine activation efficiency of FeOOH for efficient organic pollutants removal. The results indicated that the Cu doping significantly enhanced catalytic activity of FeOOH, and the Cu-FeOOH with moderate Cu doping level (15-Cu-FeOOH) performed best. The 15-Cu-FeOOH enabled almost complete removal of atrazine within 30 min, whose reaction rate (0.18 min−1) was 233.6 times higher than that of pristine FeOOH (7.8 ×10−4 min−1). Additionally, 15-Cu-FeOOH/chlorine system demonstrated universal performance towards diverse organic pollutants, extremely low metal leaching and satisfactory cyclic performance. Quenching and probe experiments elucidated •OH primarily contributed to pollutant degradation, while •Cl and •ClO played subordinate roles. Mechanistic insights revealed that the incorporated Cu+ and oxygen vacancy (Ov) synergistically enhanced performance of Cu-FeOOH: Cu+ enabled efficient Fe3+/Fe2+ cycling via formed Cu-O-Fe bond while Ov expedited Cu2+/Cu+ cycling through Cu-Ov interaction for Cu+ recovery, thus resulting in sustained chlorine activation to produce powerful reactive species for pollutant degradation.