Dichlorine monoxide (Cl
2O) is an overlooked but highly reactive free chlorine species capable of degrading recalcitrant organic pollutants in water. A recently proposed strategy introduces free chlorine (mainly HOCl/OCl
−) directly in high chloride-containing wastewater to facilitate the in situ formation of Cl
2O to degrade recalcitrant organic pollutants. In this study, the transformation of dissolved organic matter (DOM) and representative model compounds by Cl
2O was systematically investigated, along with the corresponding generation of chloro-organic byproducts and the associated genotoxicity. Cl
2O showed limited reactivity toward 3-hydroxybutyric acid and methoxyacetic acid, two aliphatic model compounds of DOM, while remaining highly reactive with resorcinol, 3-hydroxybenzoic acid, uracil, L-tyrosine, and sorbic acid, with second-order rate constants towards Cl
2O (k
Cl2O) approximately 1–6 orders of magnitudes higher than those toward Cl
2 (k
Cl2), HOCl (k
HOCl) and ClO
− (k
ClO−). Among these five model compounds reactive with Cl
2O, the formation of known chloro-organic byproducts was confirmed for resorcinol, 3-hydroxybenzoic acid, and uracil, whereas Cl
2O contributed little when reacting with L-tyrosine and sorbic acid. Mechanistic investigation using non-targeted screening of transformation products by ultra-high-performance liquid chromatography with quadrupole time-of-flight mass spectrometry (UPLC-QTOF-MS) revealed that Cl
2O is more likely to react through chlorination pathways with resorcinol, while reacting through non-chlorination pathways (e.g., oxidation) with L-tyrosine. Fourier transform-ion cyclotron resonance-mass spectrometry (FT-ICR-MS)-based non-targeted analysis was applied to track molecular-level changes of DOM and the formation of unknown chloro-organic byproducts in reactions with Cl
2O. Compared to the scenario without Cl
2O, the presence of Cl
2O resulted in a significant decrease in the number and total intensity of unknown chloro-organic byproducts (8.76-fold and 12.54-fold decreases, respectively, for landfill leachate DOM, and 2.09-fold and 1.77-fold decreases, respectively, for saline sewage DOM). Cl
2O was found to preferentially react with DOM moieties exhibiting high aromaticity, producing compounds with a higher degree of oxidation. Cl
2O also facilitated ring cleavage of nitrogen-containing aromatic moieties, as evidenced by the formation of compounds with reduced aromaticity. In addition, the presence of Cl
2O reduced the genotoxicity of landfill leachate DOM by approximately 45% and maintained comparable genotoxicity levels when reacting with saline sewage DOM relative to the scenario without Cl
2O. The findings of this study highlight the merits of using Cl
2O to effectively degrade organic pollutants, suppress the formation of chloro-organic byproducts arising from reactions with DOM, and reduce overall toxicity in high chloride-containing wastewaters. In addition, the study advances the fundamental understanding of Cl
2O-mediated transformation mechanisms of organic compounds.
| Date of Award | 2025 |
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| Original language | English |
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| Awarding Institution | - The Hong Kong University of Science and Technology
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| Supervisor | Chii SHANG (Supervisor) |
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