ABSTRACT:In our previous studies, a synthesized Fe−Mn binary oxide was found to be very effective for both As(V) and As(III) removal in aqueous phase, because As(III) could be easily oxidized to As(V). As(III) oxidation and As(V) sorption by the Fe−Mn binary oxide may also play an important role in the natural cycling of As, because of its common occurrence in the environment. In the present study, the respective role of Fe and Mn contents present in the Fe−Mn binary oxide on As(III) removal was investigated via a direct in situ determination of arsenic speciation using X-ray absorption spectroscopy. X-ray absorption near edge structure results indicate that Mn atoms exist in a mixed valence state of +3 and +4 and further confirm that MnO x (1.5 < x < 2) content is mainly responsible for oxidizing As(III) to As(V) through a two-step pathway [reduction of Mn(IV) to Mn(III) and subsequent Mn(III) to Mn(II)] and FeOOH content is dominant for adsorbing the formed As(V). No significant As(III) oxidation by pure FeOOH had been observed during its sorption, when the system was exposed to air. The extended X-ray absorption fine structure results reveal that the As surface complex on both the As(V)-and As(III)-treated sample surfaces is an inner-sphere bidentate binuclear corner-sharing complex with an As−M (M = Fe or Mn) interatomic distance of 3.22−3.24 Å. In addition, the MnO x and FeOOH contents exist only as a mixture, and no solid solution is formed. Because of its high effectiveness, low cost, and environmental friendliness, the Fe−Mn binary oxide would play a beneficial role as both an efficient oxidant of As(III) and a sorbent for As(V) in drinking water treatment and environmental remediation.
■ INTRODUCTIONArsenic, a ubiquitous trace element in the aquatic environment, is introduced from both natural processes and anthropogenic sources. 1 In natural water, arsenic is mostly found in two inorganic forms, namely, arsenate and arsenite. In welloxygenated water, As(V) is the major arsenic species, while As(III) is dominant in reduced groundwater. As(III) is more toxic, soluble, and mobile than As(V). 2,3 A high level of arsenic in groundwater and surface waters is a major concern worldwide, because of its high toxicity and carcinogenicity. To minimize the possible health risks, the World Health Organization (WHO) has set a stringent limit of 10 μg L −1 As for drinking water. 4 The adsorption reactions between arsenic and minerals (particularly metal oxides) play a very important role in its mobility and potential bioavailability because arsenic can be strongly adsorbed onto the surface of metal oxides, such as iron (hydr)oxides, alumina, and manganese oxides, which commonly occur in the aquatic environment. 5,6 Adsorption is also regarded as a promising method for the removal of arsenic from water, owing to its simple operation, high efficiency, and cost effectiveness. Numerous investigations have focused on arsenic immobilization by natural and synthetic Fe (hydr)oxides and Fe-containing materials. 7−10 Recently,...