Mechanisms for simultaneous ozonation of sulfamethoxazole and natural organic matters in secondary effluent from sewage treatment plant

• Published in: Frontiers of environmental science & engineering 2021-08, Vol.15 (4), p.75, Article 75
• Main Authors: Liu, Xinshu, Su, Xiaoman, Tian, Sijie, Li, Yue, Yuan, Rongfang
• Format: Article
• Language: English
• Subjects: Antibiotics; Aromaticity; Degradation; Degradation mechanism; Degradation products; Earth and Environmental Science; Effluents; Environment; Hydroxylation; Natural organic matters; Oxidation; Ozonation; Research Article; Ring opening; Secondary effluent; Sewage effluents; Sewage treatment plants; Sulfamethoxazole; Wastewater treatment plants; Water treatment
• ISSN: 2095-2201; 2095-221X
• DOI: 10.1007/s11783-020-1368-0

* SMX was mainly degraded by hydrolysis, isoxazole oxidation and double-bond addition. * Isoxazole oxidation and bond addition products were formed by direct ozonation. * Hydroxylated products were produced by indirect oxidation. * NOM mainly affected the degradation of SMX by consuming *OH rather than O 3. * Inhibitory effect of NOM on SMX removal was related to the components' aromaticity. Sulfamethoxazole (SMX) is commonly detected in wastewater and cannot be completely decomposed during conventional treatment processes. Ozone (O 3) is often used in water treatment. This study explored the influence of natural organic matters (NOM) in secondary effluent of a sewage treatment plant on the ozonation pathways of SMX. The changes in NOM components during ozonation were also analyzed. SMX was primarily degraded by hydrolysis, isoxazole-ring opening, and double-bond addition, whereas hydroxylation was not the principal route given the low maximum abundances of the hydroxylated products, with m/z of 269 and 287. The hydroxylation process occurred mainly through indirect oxidation because the maximum abundances of the products reduced by about 70% after the radical quencher was added, whereas isoxazole-ring opening and double-bond addition processes mainly depended on direct oxidation, which was unaffected by the quencher. NOM mainly affected the degradation of micropollutants by consuming *OH rather than O 3 molecules, resulting in the 63%-85% decrease in indirect oxidation products. The NOM in the effluent were also degraded simultaneously during ozonation, and the components with larger aromaticity were more likely degraded through direct oxidation. The dependences of the three main components of NOM in the effluent on indirect oxidation followed the sequence: humic-like substances>fluvic-like substances>protein-like substances. This study reveals the ozonation mechanism of SMX in secondary effluent and provides a theoretical basis for the control of SMX and its degradation products in actual water treatment.