Manganese oxide has been widely investigated for oxidation of arsenite (As(III)) to arsenate (As(V)) due to its high redox potential; however, it becomes extremely unstable after reuse. Here, As(III) oxidation activity and stability of manganese oxide in the presence of peroxymonosulfate (PMS) is investigated. Batch experimental results reveal that manganese oxide/PMS exhibits high catalytic activity for As(III) oxidation compared to manganese oxide or PMS alone. Addition of PMS to manganese oxide not only reveals long-term stability for As(III) oxidation, but also shows high As(III) oxidation activity in the presence of coexisting ions such as As(V) and phosphate. Quenching tests reveal that As(III) oxidation in the manganese oxide/PMS system is attributed to activation of PMS by manganese oxide at different oxidation states (Mn(III) and Mn(IV)), and the generation of sulfate radicals that are responsible for As(III) oxidation. exist in polluted groundwater. Between them, As(III) is reportedly more harmful than As(V) due to its greater mobility and toxicity. [4] Therefore, oxidation of As(III) to As(V) is not only a possible approach to reducing arsenic impacts on human health, but also is a vital step for total arsenic immobilization prior to treatment by subsequent technologies such as sorption and coprecipitation. [5] Manganese oxide has been widely used for rapid oxidation of As(III) to As(V) due to its high redox potential of E 0 (MnO 2 / Mn 2+ ) = 1.22 V. [6][7][8][9][10][11][12][13][14][15] However, to our knowledge, manganese oxide is unstable after being reused for As(III) oxidation, which is attributed to the release of Mn 2+ during As(III) oxidation and a decrease in the Mn oxidation state. [8,9] This means that manganese oxide only acts as an oxidant for As(III) oxidation, rather than as a catalyst. In addition, a reduction in oxidation activity may occur in the presence of coexisting ions such as phosphate in arsenic-containing wastewater. [14][15][16][17] This is due to the favorable adsorption of coexisting ions onto manganese oxide surfaces, which then occupy and passivate its surface active sites. [16] Therefore, a strategy to improve As(III) oxidation rate and guarantee the recycling of manganese oxide activity is still required.Peroxymonosulfate (PMS, HSO 5 − ) is one form of peroxosulfate-based chemical that has been widely used as an oxidant in different advanced oxidation process (AOP) techniques for degradation of organic pollutants, which has been used to quickly oxidize As(III) to As(V) in recent works. [18,19] Due to the low As(III) oxidation rate of PMS at room temperature, there is still a need to activate PMS forming sulfate radicals (SO 4 −• ) with high redox potential (2.5-2.8 V). In peroxosulfate-based AOP systems, sulfate radicals (SO 4 −• ) can be formed through activation of PMS by UV, heat, and catalysts. [20][21][22] For example, peroxosulfate-based chemicals activated by UV and Fe 2+ rapidly oxidized As(III). [18,23] As a result of lower energy consumption and its recycling ...