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环境水中布洛芬衍生物的光降解和臭氧化:动力学方法及矿化和可生物降解性评估。

Photodegradation and ozonation of ibuprofen derivatives in the water environment: Kinetics approach and assessment of mineralization and biodegradability.

机构信息

Łukasiewicz Research Network - Textile Research Institute, Brzezińska 5/15, 92-103, Łódź, Poland.

Łukasiewicz Research Network - Textile Research Institute, Brzezińska 5/15, 92-103, Łódź, Poland.

出版信息

Chemosphere. 2022 Mar;291(Pt 1):132742. doi: 10.1016/j.chemosphere.2021.132742. Epub 2021 Nov 1.

DOI:10.1016/j.chemosphere.2021.132742
PMID:34736944
Abstract

This article presents the results of studies on the degradation of ibuprofen transformation products: 1-hydroxyibuprofen (1OHIBF), 4-ethylbenzaldehyde (4EBA), 1-[4-(2-methylpropyl)phenyl]ethan-1-ol (MPPE) in water. To the best of our knowledge, this is the first paper where the ozonation and photodegradation (VIS and UV photolysis, degradation in HO/UV system, photosensitized oxidation) of 1OHIBF, 4EBA and MPPE are reported. The processes were performed in demineralized and natural river water. The influence of various reaction parameters on the removal degree was checked. Both, photolysis under VIS light and photosensitized oxidation of target compounds are very low-efficient processes. Ozonation and degradation in HO/UV system are effective methods for ibuprofen derivatives degradation. Components present in river water reduced removal degree of investigated compounds during ozonation and degradation in HO/UV system. The biodegradability assessment using the Average Oxidation State (AOS) and COD/TOC ratio proved the formation of more oxidized by-products during both processes. The determined second-order rate constants for ozone reaction with 1OHIBF, 4EBA and MPPE are 0.1 ± 0.01, 10.95 ± 1.36 and 3.04 ± 0.33 M s, respectively. The calculated reaction rate constants of hydroxyl radicals with MPPE, 4EBA and 1OHIBF are 3.57 × 10, 6.83 × 10 and 1.06 × 10 M s, respectively.

摘要

本文介绍了布洛芬转化产物(1-羟基布洛芬(1OHIBF)、4-乙基苯甲醛(4EBA)、1-[4-(2-甲基丙基)苯基]乙烷-1-醇(MPPE))在水中降解的研究结果。据我们所知,这是第一篇报道 1OHIBF、4EBA 和 MPPE 的臭氧化和光降解(VIS 和 UV 光解、HO/UV 系统降解、光敏氧化)的论文。这些过程是在去矿物质和天然河水中进行的。检查了各种反应参数对去除程度的影响。可见光下的光解和目标化合物的光致氧化都是非常低效的过程。臭氧化和 HO/UV 系统中的降解是布洛芬衍生物降解的有效方法。河水中存在的成分降低了臭氧氧化和 HO/UV 系统中降解过程中研究化合物的去除程度。使用平均氧化态(AOS)和 COD/TOC 比进行的生物降解性评估证明了在这两个过程中形成了更多氧化的副产物。臭氧与 1OHIBF、4EBA 和 MPPE 的反应的确定二级速率常数分别为 0.1±0.01、10.95±1.36 和 3.04±0.33 M s。计算得到的 MPPE、4EBA 和 1OHIBF 与羟基自由基的反应速率常数分别为 3.57×10、6.83×10 和 1.06×10 M s。

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