{"title":"Reaction kinetics of organic sulfur compounds with ozone in aqueous phase","authors":"Simon A. Rath, Maria Lia Halder, Urs von Gunten","doi":"10.1016/j.watres.2025.124649","DOIUrl":null,"url":null,"abstract":"Sulfur functional groups are abundant in natural organic compounds, pesticides and pharmaceuticals. Kinetic data of their aqueous reaction with ozone is only available for a very small set of compounds and sometimes contradictory, making predictions on their fate during ozonation processes difficult. Therefore, second-order rate constants <em>k</em><sub>O₃</sub> were determined for 37 sulfur-containing compounds and trends in reactivity were identified. For the determination of <em>k</em><sub>O₃</sub> via competition kinetics, aldicarb was established as pH-independent competitor (<em>k</em><sub>O₃</sub>=1.0 × 10⁶M⁻¹s⁻¹). Sulfides (thioethers) react very fast with ozone (<em>k</em><sub>O₃</sub>≈2 × 10⁶M⁻¹s⁻¹). Exceptions are sulfides, which are π-conjugated to electron-withdrawing groups (e.g., thiocarbamates, <em>k</em><sub>O₃</sub>≈10⁰−10³M⁻¹s⁻¹), and β-lactam antibiotics (<em>k</em><sub>O₃</sub>≈10³M⁻¹s⁻¹), which are deactivated to different degrees. Thiols exhibit pH-dependent reactivities, though the dependency is much smaller than previously reported, ranging from <em>k</em><sub>O₃+SH</sub>≈10<sup>4</sup>M⁻¹s⁻¹ to <em>k</em><sub>O₃+S⁻</sub>≈10⁶M⁻¹s⁻¹, but an unprecedented pH-dependency is observed. A deactivating effect of neighboring groups renders the reactivity of the disulfide cystine and similar compounds pH-dependent (<em>k</em><sub>O₃</sub>(pH3)≈10²M⁻¹s⁻¹, <em>k</em><sub>O₃</sub>(pH7)≈10⁵M⁻¹s⁻¹) while disulfides without acidic functional groups exhibit pH-independent reactivity (<em>k</em><sub>O₃</sub>≈2 × 10⁵M⁻¹s⁻¹). Further oxidized functional groups like sulfoxides or thiosulfinate esters are unreactive (<em>k</em><sub>O₃</sub>≈10⁰−10¹M⁻¹s⁻¹), but sulfinates are very susceptible to ozonation (<em>k</em><sub>O₃</sub>≈2 × 10⁶M⁻¹s⁻¹). A definitive explanation for this difference is still lacking. For non-<em>N</em>-alkylated isothiazolones, an unexpected pH-dependency is observed, similar to cysteines. The reactivity at pH 7 differs by 4 orders of magnitude, whether or not <em>N</em>-alkylated (<em>k</em><sub>O₃</sub>≈10²M⁻¹s⁻¹, <em>k</em><sub>O₃</sub>≈10⁶M⁻¹s⁻¹, respectively). Overall, the data presented provides novel insights into the ozone reactivity of sulfur compounds as a basis for a better assessment of their fate during ozonation.","PeriodicalId":443,"journal":{"name":"Water Research","volume":"90 1","pages":""},"PeriodicalIF":12.4000,"publicationDate":"2025-09-23","publicationTypes":"Journal Article","fieldsOfStudy":null,"isOpenAccess":false,"openAccessPdf":"","citationCount":"0","resultStr":null,"platform":"Semanticscholar","paperid":null,"PeriodicalName":"Water Research","FirstCategoryId":"93","ListUrlMain":"https://doi.org/10.1016/j.watres.2025.124649","RegionNum":1,"RegionCategory":"环境科学与生态学","ArticlePicture":[],"TitleCN":null,"AbstractTextCN":null,"PMCID":null,"EPubDate":"","PubModel":"","JCR":"Q1","JCRName":"ENGINEERING, ENVIRONMENTAL","Score":null,"Total":0}
引用次数: 0
Abstract
Sulfur functional groups are abundant in natural organic compounds, pesticides and pharmaceuticals. Kinetic data of their aqueous reaction with ozone is only available for a very small set of compounds and sometimes contradictory, making predictions on their fate during ozonation processes difficult. Therefore, second-order rate constants kO₃ were determined for 37 sulfur-containing compounds and trends in reactivity were identified. For the determination of kO₃ via competition kinetics, aldicarb was established as pH-independent competitor (kO₃=1.0 × 10⁶M⁻¹s⁻¹). Sulfides (thioethers) react very fast with ozone (kO₃≈2 × 10⁶M⁻¹s⁻¹). Exceptions are sulfides, which are π-conjugated to electron-withdrawing groups (e.g., thiocarbamates, kO₃≈10⁰−10³M⁻¹s⁻¹), and β-lactam antibiotics (kO₃≈10³M⁻¹s⁻¹), which are deactivated to different degrees. Thiols exhibit pH-dependent reactivities, though the dependency is much smaller than previously reported, ranging from kO₃+SH≈104M⁻¹s⁻¹ to kO₃+S⁻≈10⁶M⁻¹s⁻¹, but an unprecedented pH-dependency is observed. A deactivating effect of neighboring groups renders the reactivity of the disulfide cystine and similar compounds pH-dependent (kO₃(pH3)≈10²M⁻¹s⁻¹, kO₃(pH7)≈10⁵M⁻¹s⁻¹) while disulfides without acidic functional groups exhibit pH-independent reactivity (kO₃≈2 × 10⁵M⁻¹s⁻¹). Further oxidized functional groups like sulfoxides or thiosulfinate esters are unreactive (kO₃≈10⁰−10¹M⁻¹s⁻¹), but sulfinates are very susceptible to ozonation (kO₃≈2 × 10⁶M⁻¹s⁻¹). A definitive explanation for this difference is still lacking. For non-N-alkylated isothiazolones, an unexpected pH-dependency is observed, similar to cysteines. The reactivity at pH 7 differs by 4 orders of magnitude, whether or not N-alkylated (kO₃≈10²M⁻¹s⁻¹, kO₃≈10⁶M⁻¹s⁻¹, respectively). Overall, the data presented provides novel insights into the ozone reactivity of sulfur compounds as a basis for a better assessment of their fate during ozonation.
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.