Dissociation-dependent kinetics and distinct pathways for direct photolysis and •OH/SO4•− radical dominated photodegradation of ionizable antiviral drugs in aquatic systems

IF 12.4 1区 环境科学与生态学 Q1 ENGINEERING, ENVIRONMENTAL Water Research Pub Date : 2025-03-09 DOI:10.1016/j.watres.2025.123452
Nannan Cui , Linke Ge , Crispin Halsall , Junfeng Niu , Jinshuai Zheng , Peng Zhang
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Abstract

Advanced oxidation processes (AOPs), such as UV, UV/H2O2 and UV/persulfate, are widely used to remove emerging organic contaminants from wastewater streams. However, knowledge on chemical degradation pathways, reaction kinetics as well as formation and toxicity of key degradates is limited. We investigated the direct photolysis and •OH/SO4•− dominated kinetics, intermediates and toxicity evolution of three ionizable antiviral drugs (ATVs): tenofovir (TFV), didanosine (DDI), and nevirapine (NVP). Their transformation kinetics were found to depend on the dominant protonated states. Under UV–Vis irradiation (λ > 290 nm), TFV and DDI photolyzed the fastest in the cationic forms (H2TFV+ and H2DDI+), whereas NVP exhibited the fastest photodegradation in the anionic forms (NVP). The anionic forms (TFV and NVP) demonstrated the highest reactivities towards •OH in most cases, while the cationic forms (H2DDI+ and H2NVP+) reacted the fastest with SO4•− for most of the ATVs. The dissociation-dependent kinetics can be attributed to the discrepancies in deprotonation degrees, quantum yields, electron densities and coulombic repulsion with SO4•− in their dissociated forms. Based on the key product identification via HPLC-MS/MS, the pathways involved hydroxylation, dehydroxylation, oxidation, reduction, cyclopropyl cleavage, C-N breaking, elimination, cyclization and deamidation reactions, which can be prioritized based on the specific compound and the photochemical process. Furthermore, a bioassay showed the photomodified toxicity of the ATVs to Vibrio fischeri (bioluminescent bacteria) during the three processes, which was also demonstrated by ECOSAR model assessment. Nearly half of the chemical intermediates were demonstrably more toxic than their respective parent ATVs. These results provide new insights into understanding the persistence, fate and hazards associated with applying the UV-assisted AOPs to treat wastewater containing ATVs.

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可离子化抗病毒药物在水生系统中直接光解和 OH/SO4- 自由基主导光降解的解离依赖动力学和不同途径
高级氧化工艺(AOPs),如UV, UV/H2O2和UV/过硫酸盐,被广泛用于去除废水中新出现的有机污染物。然而,对化学降解途径、反应动力学以及关键降解物的形成和毒性的了解有限。研究了替诺福韦(TFV)、二腺苷(DDI)和奈韦拉平(NVP)三种可电离抗病毒药物(ATVs)的直接光解和•OH/SO4•−主导动力学、中间体和毒性演变。发现它们的转化动力学依赖于主要的质子化态。紫外可见照射下(λ >;290 nm), TFV和DDI以阳离子形式(H2TFV+和H2DDI+)的光降解速度最快,而NVP以阴离子形式(NVP−)的光降解速度最快。在大多数情况下,阴离子形式(TFV -和NVP -)对•OH的反应活性最高,而阳离子形式(H2DDI+和H2NVP+)对大多数atv的反应速度最快。离解相关动力学可归因于离解态SO4•−的去质子化程度、量子产率、电子密度和库仑斥力的差异。通过HPLC-MS/MS对关键产物进行鉴定,主要途径包括羟基化、去羟基化、氧化、还原、环丙基裂解、C-N断裂、消除、环化和脱酰胺反应,可根据具体化合物和光化学过程进行优先排序。此外,生物测定显示,在这三个过程中,ATVs对费氏弧菌(生物发光细菌)的毒性也得到了ECOSAR模型评估的证实。近一半的化学中间体明显比它们各自的母体atv毒性更大。这些结果为理解紫外辅助AOPs处理含atv废水的持久性、命运和危害提供了新的见解。
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来源期刊
Water Research
Water Research 环境科学-工程:环境
CiteScore
20.80
自引率
9.40%
发文量
1307
审稿时长
38 days
期刊介绍: Water Research, along with its open access companion journal Water Research X, serves as a platform for publishing original research papers covering various aspects of the science and technology related to the anthropogenic water cycle, water quality, and its management worldwide. The audience targeted by the journal comprises biologists, chemical engineers, chemists, civil engineers, environmental engineers, limnologists, and microbiologists. The scope of the journal include: •Treatment processes for water and wastewaters (municipal, agricultural, industrial, and on-site treatment), including resource recovery and residuals management; •Urban hydrology including sewer systems, stormwater management, and green infrastructure; •Drinking water treatment and distribution; •Potable and non-potable water reuse; •Sanitation, public health, and risk assessment; •Anaerobic digestion, solid and hazardous waste management, including source characterization and the effects and control of leachates and gaseous emissions; •Contaminants (chemical, microbial, anthropogenic particles such as nanoparticles or microplastics) and related water quality sensing, monitoring, fate, and assessment; •Anthropogenic impacts on inland, tidal, coastal and urban waters, focusing on surface and ground waters, and point and non-point sources of pollution; •Environmental restoration, linked to surface water, groundwater and groundwater remediation; •Analysis of the interfaces between sediments and water, and between water and atmosphere, focusing specifically on anthropogenic impacts; •Mathematical modelling, systems analysis, machine learning, and beneficial use of big data related to the anthropogenic water cycle; •Socio-economic, policy, and regulations studies.
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