Environment Research Institute, Shandong University, Qingdao, 266200, PR China.
School of Environmental Science and Engineering, Shandong University, Qingdao, 266200, PR China.
Environ Pollut. 2022 Dec 15;315:120416. doi: 10.1016/j.envpol.2022.120416. Epub 2022 Oct 11.
2-(2'-hydroxy-5'-methylphenyl) benzotriazole (UV-P) is a type of emerging persistent organic pollutant that is reported harmful to organisms. However, its degradation mechanisms and transformation behaviors in aquatic environments are not yet clear, which are significant for better understanding its environmental fate and potential toxicological impacts. In present work, the degradation mechanisms, kinetics, half-life times and eco-toxicity assessment of UV-P initiated by hydroxyl radical (•OH), sulfate radical (SO•), and singlet oxygen (O) are systematically studied using density functional theory (DFT) and experimental methods. The initiated reaction results show that benzene ring of UV-P is vulnerable to attack by •OH, while benzotriazole is easily attacked by SO•. The kinetic calculations indicate that •OH-addition reaction R15 is dominant initial pathway. And the half-life (t) of UV-P is calculated according to rate constants, t decreases rapidly with [ROS] increasing. UV-P exhibits environmental persistence when [•OH] ≤ 10 M. The subsequent degradation mechanisms of hydroxylated UV-P react with •OH and O are also calculated. A novel ring-opening reaction channel is proposed that O-addition intermediate combines with hydroperoxyl radical (HO•) to cleave aromatic ring. The rate-determining step is intramolecular dehydration reaction with the energy barrier of 32.98 kcal mol and 41.13 kcal mol to cleave benzene ring and benzotriazole ring, respectively. The degradation experiments of UV-P are conducted in CoO activated potassium peroxymonosulfate (PMS) system, and liquid chromatograph-mass spectrometer (LC-MS) results identified that dihydroxylated species are main intermediates, which is consistent with theoretical calculation results. Furthermore, the eco-toxicity assessment shows that the acute and chronic toxicities of most degradation products are reduced compared with UV-P, however, their toxicity levels still keep at toxic and harmful. The environmental risk of UV-P deserves more attention.
2-(2'-羟基-5'-甲基苯基)苯并三唑(UV-P)是一种新兴的持久性有机污染物,据报道对生物体有害。然而,其在水生环境中的降解机制和转化行为尚不清楚,这对于更好地了解其环境归宿和潜在的毒理学影响至关重要。在本工作中,采用密度泛函理论(DFT)和实验方法系统研究了羟基自由基(•OH)、硫酸根自由基(SO•)和单线态氧(O)引发的 UV-P 的降解机制、动力学、半衰期和生态毒性评估。引发反应结果表明,UV-P 的苯环易受•OH 攻击,而苯并三唑易受 SO•攻击。动力学计算表明,•OH-加成反应 R15 是主导的初始途径。根据速率常数计算 UV-P 的半衰期(t),随着[ROS]的增加,t 迅速减小。当[•OH]≤10 M 时,UV-P 表现出环境持久性。随后还计算了羟化 UV-P 与•OH 和 O 反应的后续降解机制。提出了一种新的开环反应通道,即 O-加成中间体与过氧氢自由基(HO•)结合,使芳环断裂。速率决定步骤是分子内脱水反应,其能量势垒分别为 32.98 kcal/mol 和 41.13 kcal/mol,以分别断裂苯环和苯并三唑环。在 CoO 激活过一硫酸盐(PMS)体系中进行了 UV-P 的降解实验,液相色谱-质谱(LC-MS)结果鉴定出二羟基化产物是主要中间体,与理论计算结果一致。此外,生态毒性评估表明,与 UV-P 相比,大多数降解产物的急性和慢性毒性降低,但它们的毒性水平仍处于有毒和有害的水平。UV-P 的环境风险值得更多关注。