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6PPD-quinone degradation by unactivated peroxymonosulfate via direct oxidation and enhanced generation of 1O2

文献类型： 外文期刊

作者： Yu, Haibin 1 ; Wu, Nannan 1 ; Liu, Zhenzhen 1 ; Zhao, Huiyu 1 ; Di, Shanshan 1 ; Wang, Zhiwei 1 ; Gu, Chengbo 1 ; Wang, Xinquan 1 ; Qi, Peipei 1 ;

作者机构： 1.Zhejiang Acad Agr Sci 6 5, Inst Agroprod Safety & Nutr, State Key Lab Managing Biot & Chem Threats Qual &, Hangzhou 310021, Peoples R China

2.Northeast Forestry Univ, Coll Chem, Engn Res Ctr Forest Biopreparat, State Key Lab Forest Plant Ecol,Minist Educ,Heilon, Harbin 150040, Peoples R China

关键词： 6PPD-quinone; Unactivated peroxymonosulfate; Singlet oxygen; Degradation mechanism; Theoretical calculation

期刊名称：CHEMICAL ENGINEERING JOURNAL （ 影响因子：13.2； 五年影响因子：13.5 ）

ISSN： 1385-8947

年卷期： 2025 年 505 卷

页码：

收录情况： SCI

摘要： N-(1,3-dimethylbutyl)-N'-phenyl-p-phenylenediamine-quinone (6PPDQ) is extremely toxic to aquatic organisms, which has attracted extensive attention. Hence, the degradation of 6PPDQ from aquatic environments is currently one of the urgent environmental issues to be addressed. In this work, peroxymonosulfate (PMS) was used to degrade 6PPDQ without activators avoiding some constraints such as high energy consumption and introduction of secondary pollution. 1O2 was an important active species in the degradation of 6PPDQ by PMS without activation. 6PPDQ could increase production yield of 1O2, which further degraded 6PPDQ. Contributions of 1O2 and direct PMS oxidation to 6PPDQ degradation varied with pH values (79% and 21% at pH = 9.0, respectively). The increase of temperature, PMS initial concentration and pH values was conducive to improve the degradation efficiency of 6PPDQ. HCO3- and Fe3+ significantly accelerated the degradation of 6PPDQ with complete degradation within 60 min. In addition, two degradation pathways containing 8 intermediates were proposed, which mainly involved C-N bond cleavage and hydroxyl addition. Additionally, theoretical calculations demonstrated the high reactivity of N atoms on 6PPDQ, supporting that degradation intermediates were primarily formed through reactions involving N atoms. Meanwhile, the toxicity evaluation of reaction products indicated that transformation products were all less toxic than 6PPDQ, suggesting a process of decreasing toxicity. These results demonstrate the potential application of removing 6PPDQ by unactivated PMS from environmental waters.

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