Abstract

The O3/PMS system has appeared as an effective wastewater treatment method because of the simultaneous generation of hydroxyl radicals (•OH) and sulfate radicals (SO4•−). Many research achievements have been made on the degradation of micropollutants and the reaction mechanism of the O3/PMS system. However, an integral understanding of the O3/PMS system is lacking, which limits the development of safe and effective AOP-based water treatment schemes. Therefore, in this review, the degradation effects, toxicity changes, and reaction mechanisms of various micropollutants in the O3/PMS system are reviewed. The formation of oxidation by-products (OBPs) is an important issue that affects the practical application of O3/PMS systems. The formation mechanism and control methods of OBPs in the O3/PMS system are overviewed. In addition, the influence of different reaction conditions on the O3/PMS system are comprehensively evaluated. Finally, future research needs are proposed based on the limited understanding of O3/PMS systems in the degradation of micropollutants and formation of OBPs. Specifically, the formation rules of several kinds of OBPs during the O3/PMS system are not completely clear yet. Furthermore, pilot-scale research, the operational costs, sustainability, and general feasibility of the O3/PMS system also need to be studied. This review can offer a comprehensive assessment on the O3/PMS system to fill the knowledge gap and provide guidance for the future research and engineering applications of the O3/PMS system. Through this effort, the O3/PMS system can be better developed and turned towards practical applications.

Highlights

  • At present, the emergence of some pollutants pose a threat to water quality and safety, which has aroused widespread concern [1,2,3]

  • Sulfate radicals (SO4 − )-based advanced oxidation processes (AOPs) have received widespread attention owing to their strong oxidation ability, fast reaction rate, and wide applicability to contaminants in wastewater [4,5,6]

  • OH produced in the process of O3 decomposition is a non-selective strong oxidant (Equations (1) and (2)), which can rapidly react with various micropollutants at nearly diffusion-controlled rates, and the diffusion-controlled rate of

Read more

Summary

Introduction

The emergence of some pollutants (such as drugs, personal care products, endocrine disruptors, and other refractory organics) pose a threat to water quality and safety, which has aroused widespread concern [1,2,3]. The study of Andrés et al indicated that the O3 /PMS combination produced a synergistic effect in the inactivation of microorganisms [18] All these studies have shown that the O3 /PMS system has a very great application potential in water treatment. O3 -activated PMS enhanced the degradation of pCBA, proving that PMS had a similar effect as H2 O2 in promoting the generation of free radicals during ozonation [16]. The research by Yuan et al indicated that no radical activated PMS enhanced the degradation of pCBA, proving that PMS had a similar effect as H2O2 in promoting the generation of free radicals during ozonation [16]. Represents the fission position of O–O bond for the formation of sulfate radicals

Mechanism
Influencing Factors
Degradation Effect and Energy Efficiency
Toxicity Changes and Degradation Pathway
Formation Pathway and Influencing Factors
Control Strategy
The mechanism of theofinhibition of bromate formation
Recommendations and Future Prospects
Findings
Conclusions
Full Text
Published version (Free)

Talk to us

Join us for a 30 min session where you can share your feedback and ask us any queries you have

Schedule a call