Xiaohong Ma, Shiqing Cao, Xiaoqian Feng, Yingying Wu, Xuechang Ren*, Song Yang and Libang Ma*,
{"title":"Comparative Study of Four Polyphenols with Enhanced Fe3+/H2O2 Fenton-like Activity for Degrading Phenanthrene over a Wide Initial pH Range","authors":"Xiaohong Ma, Shiqing Cao, Xiaoqian Feng, Yingying Wu, Xuechang Ren*, Song Yang and Libang Ma*, ","doi":"10.1021/acsestwater.4c0076710.1021/acsestwater.4c00767","DOIUrl":null,"url":null,"abstract":"<p >Polyphenol (PP)-enhanced Fe<sup>3+</sup>/H<sub>2</sub>O<sub>2</sub> oxidation presents a promising solution to the traditional Fenton process limitations, including acidic pH requirements, restricted Fe<sup>3+</sup>/Fe<sup>2+</sup> cycling, and low H<sub>2</sub>O<sub>2</sub> stability. The type of PP and the initial pH are key factors influencing Fenton-like reactions by affecting iron complexation and reduction. This study evaluates catechol, protocatechuic acid (PCA), gallic acid (GA), and tannic acid (TA) to enhance phenanthrene (PHE) degradation via the Fe<sup>3+</sup>/H<sub>2</sub>O<sub>2</sub> process over a wide initial pH range. GA achieved the highest PHE removal rates, which can be attributed to its unique third ortho-hydroxyl group. The significant improvement in PHE degradation observed with adding PPs can be ascribed to their ability to form complexes with Fe<sup>3+</sup>, promote cycling between Fe<sup>3+</sup> and Fe<sup>2+</sup>, and stabilize H<sub>2</sub>O<sub>2</sub>, all of which are pH-dependent. Hydroxyl radical (<sup>•</sup>OH) and superoxide radical (O<sub>2</sub><sup>•–</sup>) were identified as the primary species responsible for PHE degradation in the Fe<sup>3+</sup>/PP/H<sub>2</sub>O<sub>2</sub> systems, although their contributions varied with the specific PPs used. The degradation products of both PHE and PPs were characterized by using mass spectrometry, suggesting possible degradation pathways and associated toxicities. Overall, this study demonstrates that the PP-enhanced Fe<sup>3+</sup>/H<sub>2</sub>O<sub>2</sub> process holds significant potential for the remediation of polycyclic aromatic hydrocarbon contamination.</p>","PeriodicalId":93847,"journal":{"name":"ACS ES&T water","volume":"5 2","pages":"713–726 713–726"},"PeriodicalIF":4.8000,"publicationDate":"2025-01-02","publicationTypes":"Journal Article","fieldsOfStudy":null,"isOpenAccess":false,"openAccessPdf":"","citationCount":"0","resultStr":null,"platform":"Semanticscholar","paperid":null,"PeriodicalName":"ACS ES&T water","FirstCategoryId":"1085","ListUrlMain":"https://pubs.acs.org/doi/10.1021/acsestwater.4c00767","RegionNum":0,"RegionCategory":null,"ArticlePicture":[],"TitleCN":null,"AbstractTextCN":null,"PMCID":null,"EPubDate":"","PubModel":"","JCR":"Q1","JCRName":"ENVIRONMENTAL SCIENCES","Score":null,"Total":0}
引用次数: 0
Abstract
Polyphenol (PP)-enhanced Fe3+/H2O2 oxidation presents a promising solution to the traditional Fenton process limitations, including acidic pH requirements, restricted Fe3+/Fe2+ cycling, and low H2O2 stability. The type of PP and the initial pH are key factors influencing Fenton-like reactions by affecting iron complexation and reduction. This study evaluates catechol, protocatechuic acid (PCA), gallic acid (GA), and tannic acid (TA) to enhance phenanthrene (PHE) degradation via the Fe3+/H2O2 process over a wide initial pH range. GA achieved the highest PHE removal rates, which can be attributed to its unique third ortho-hydroxyl group. The significant improvement in PHE degradation observed with adding PPs can be ascribed to their ability to form complexes with Fe3+, promote cycling between Fe3+ and Fe2+, and stabilize H2O2, all of which are pH-dependent. Hydroxyl radical (•OH) and superoxide radical (O2•–) were identified as the primary species responsible for PHE degradation in the Fe3+/PP/H2O2 systems, although their contributions varied with the specific PPs used. The degradation products of both PHE and PPs were characterized by using mass spectrometry, suggesting possible degradation pathways and associated toxicities. Overall, this study demonstrates that the PP-enhanced Fe3+/H2O2 process holds significant potential for the remediation of polycyclic aromatic hydrocarbon contamination.