Abstract

Bromate ( BrO 3 − ) contamination in drinking water is a growing concern. Advanced reduction processes (ARPs) are reportedly promising in relieving this concern. In this work, UV/superparamagnetic BiOCl (BiOCl loaded onto superparamagnetic hydroxyapatite) assisted with small molecule carboxylic acid (formate, citrate, and acetate), a carboxyl anion radical ( CO 2 • − )-based ARP, was proposed to eliminate aqueous BrO 3 − . Formate and citrate were found to be ideal CO 2 • − precursor, and the latter was found to be safe for practical use. BrO 3 − (10 μg·L−1, WHO guideline for drinking water) can be completely degraded within 3 min under oxygen-free conditions. In this process, BrO 3 − degradation was realized by the reduction of CO 2 • − (major role) and formyloxyl radical (minor role) in bulk solution. The formation mechanism of radicals and the transformation pathway of BrO 3 − were proposed based on data on electron paramagnetic resonance monitoring, competitive kinetics, and degradation product analysis. The process provided a sustainable decontamination performance (<5% deterioration for 10 cycles) and appeared to be more resistant to common electron acceptors (O2, NO 3 − , and Fe3+) than hydrated electron based-ARPs. Phosphate based-superparamagnetic hydroxyapatite, used to support BiOCl in this work, was believed to be applicable for resolving the recycling problem of other metal-containing catalyst.

Highlights

  • As a toxic byproduct of disinfection, bromate (BrO3− ) in drinking water can find its sources from stock NaOCl and HOBr solution used as disinfectants [1], bromide (Br− ) oxidation by ozone, chlorine, or oxidative radicals (e.g., hydroxyl radical (HO·), sulfate radical (SO4− )) [2], and contaminant of hypochlorite disinfectant used in water plants [3]

  • Peaks appearing in diffraction patterns for BiOCl-HAPSM (Figure S1) can be indexed to BiOCl

  • BiOCl-HAPSM exhibited a strong UV absorption. These results clearly show that micron-sized of exhibited a strong

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Summary

Introduction

As a toxic byproduct of disinfection, bromate (BrO3− ) in drinking water can find its sources from stock NaOCl and HOBr solution used as disinfectants [1], bromide (Br− ) oxidation by ozone, chlorine, or oxidative radicals (e.g., hydroxyl radical (HO·), sulfate radical (SO4− )) [2], and contaminant of hypochlorite disinfectant used in water plants [3]. − [12,13,14]) seem to advanced reduction (involves strong reactive reducing radicals (RRRs) such as H/eaq. A popular manipulation procedure is using scavengers (Br− , SO23− , S2− , and formate) to quench ROSs to generate a system which dominated by RRRs. Our recent work concluded that the low-pressure UV photolysis of SO23− (UV-L/SO23− ) is highly suitable for practical BrO3− degradation [13]. Given the above-mentioned literature review, an UV/BiOX/SOCA process was proposed to degrade BrO3− in drinking water. This work intends to (1) probe the potential of combining photoexcited BiOX and SOCAs for CO2− generation and BrO3− removal; (2) clarify the. The influence of several common electron acceptors (O2 , NO3 , and Fe3+ ), which may the evaluate decontamination efficiency of UV/BiOX/SOCA.

Characterization of the Photocatalyst
O4 constituent
Bromate
Mechanism Clarification
Substitutes of Formate
Reusability of BiOCl-HAPSM
Influence of Common Electron Acceptors
Transformation Intermediates of
Materials and Reagents
Synthesis and Characterization of BiOCl-HAPSM
Experimental Procedures
Analysis Methods
Conclusions
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