IMPACT OF OXIDIZING AGENT ON GROUNDWATER ARSENIC TREATMENT BY AS(III), FE(II) AND MN(II) CO-OXIDATION (Invited Presentation)
In this presentation, we compare the impact of three common oxidants used in groundwater As treatment, O2, NaOCl and KMnO4, on the co-oxidation of As(III), Fe(II) and Mn(II). Oxidation experiments were performed in bicarbonate-buffered solutions at pH 7.5 using environmentally-relevant initial concentrations of 90 µM Fe(II), 9 µM Mn(II) and 0.7 µM As (50 µg/L As). The solutions were either aerated (i.e. O2 = 9 mg/L) or were mixed with stoichiometric amounts of NaOCl or KMnO4. Measurements of As, Fe and Mn removal using ICP-MS were combined with solid phase characterization by synchrotron-based As, Fe and Mn K-edge X-ray absorption spectroscopy.
We found that dosing O2 was least effective, unable to meet the 10 µg/L As guideline for any experiment, which was partly attributed to incomplete As(III) oxidation. When NaOCl was dosed, the residual As levels were always <10 µg/L and often near 1 µg/L. The addition of NaOCl completely oxidized As(III), leading to As(V) removal by sorption to Mn(III)-rich hydrous ferric oxide (HFO) in the binuclear, bridging (2C) geometry. The most effective oxidant was KMnO4, which produced even lower residual As levels than NaOCl and completely oxidized As(III), Fe(II) and Mn(II) to As(V), HFO and solid-phase MnO2. The lower residual As levels using KMnO4 were concomitant with a systematically shorter As-metal interatomic distance detected by As K-edge EXAFS shell-by-shell fits of KMnO4 samples, which is consistent with As-Mn backscattering from As(V) adsorbed to MnO2. These results suggest that KMnO4 plays a dual role in groundwater As treatment: it serves as an oxidant for As(III), Fe(II) and Mn(II) and as source of solid-phase MnO2 that can bind As(V), leading to more effective As removal.