Degradation of benzylamines during chlorination and chloramination†

IF 4.3 3区 材料科学 Q1 ENGINEERING, ELECTRICAL & ELECTRONIC ACS Applied Electronic Materials Pub Date : 2024-09-03 DOI:10.1039/D4EW00556B
Chih-Hsien Lin, Wei-Hsiang Chen and William A. Mitch
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Abstract

As widely used industrial ingredients and products of the biodegradation of benzalkonium chloride disinfectants, benzylamines are expected to occur in municipal wastewater effluents and other wastewater-impacted waters, but their fate during chlorine or chloramine disinfection is unclear. This study characterized the degradation pathways of benzylamine, N-methylbenzylamine and N,N-dimethylbenzylamine during chlorination and chloramination. The dominant reaction pathways during chlorination involved chlorine transfer to the benzylamine nitrogen followed by hydrochloric acid elimination to form an imine and hydrolysis of the imine to form an aldehyde and lower order amine. Benzylamine formed benzaldehyde in preference to benzonitrile. For N-methylbenzylamine and N,N-dimethylbenzylamine, hydrochloric acid elimination between the benzyl nitrogen and the methyl substituent formed formaldehyde and either benzylamine or N-methylbenzylamine, while elimination between the nitrogen and the benzyl substituent formed benzaldehyde and either monomethylamine or dimethylamine. Similar products were observed during chloramination, but over longer timescales. Formation of products involving halogenation of the aromatic ring was not observed. Of highest toxicological concern was the 34% molar yield of NDMA that formed during chloramination of N,N-dimethylbenzylamine in concert with benzyl alcohol by a pathway occurring in parallel to the imine formation and hydrolysis pathway. Based on these reaction pathways, a strategy to reduce NDMA formation within potable reuse facilities was validated using laboratory-scale versions of the reverse osmosis and ultraviolet light processes used in potable reuse trains. The strategy involved treating fully nitrified wastewater influents to these facilities with free chlorine for 5 min to degrade N,N-dimethylbenzylamine and other potent NDMA precursors prior to the addition of ammonia to form chloramines used to control biofouling within these facilities.

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苄胺在氯化和氯化过程中的降解
作为广泛使用的工业成分和苯扎氯铵消毒剂的生物降解产物,苄胺预计会出现在城市污水和其他受废水影响的水体中,但它们在氯消毒或氯胺消毒过程中的去向尚不清楚。这项研究描述了苄胺、N-甲基苄胺和 N,N-二甲基苄胺在氯化和氯消毒过程中的降解途径。氯化过程中的主要反应途径是氯转移到苄胺氮上,然后盐酸消除形成亚胺,亚胺水解形成醛和低阶胺。苄胺形成的苯甲醛优于苯甲腈。对于 N-甲基苄胺和 N,N-二甲基苄胺,苄基氮和甲基取代基之间的盐酸消去会形成甲醛和苄胺或 N-甲基苄胺,而氮和苄基取代基之间的消去会形成苯甲醛和一甲胺或二甲胺。在氯化过程中也观察到了类似的产物,但时间尺度更长。没有观察到涉及芳香环卤化的产物。最值得关注的毒理学问题是,在 N,N-二甲基苄胺与苄醇的氯化反应中,NDMA 的摩尔产率为 34%,其形成途径与亚胺的形成和水解途径平行。根据这些反应途径,利用实验室规模的反渗透和紫外线工艺,对减少饮用水回用设施中 NDMA 形成的策略进行了验证。该策略包括先用游离氯对这些设施的完全硝化废水进水进行 5 分钟的处理,以降解 N,N-二甲基苄胺和其他强效 NDMA 前体,然后再加入氨气形成氯胺,用于控制这些设施内的生物污垢。
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7.20
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4.30%
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567
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