Abstract
Most of the shallow aquifers ( 130 m) that still remains safe from As contamination ( 130 m) were reported as stable (mean As: wet period, 0.43 µg/L; and dry period, 0.34 µg/L), since it get less influenced by the discharge- and recharge-related seasonal variations. Speciation calculations with PHREEQC show that Siderite and Vivianite have reached the supersaturated state indicating the possibility of controlling Fe solubility by these two minerals. Low NO3 −, SO4 2−, PO4 3−, and high Fe concentrations observed in the shallow groundwater reflect the strong reducing environment of the shallow aquifer. The redox buffering could have controlled by the Fe(OH)3/Fe2+ redox pair. Laboratory leaching test confirmed that HCO3 − ion plays a vital role in releasing of As along with Fe and Al from As-affected sediment. SEM and XRD analysis indicated the presence of Fe-Al oxyhydroxide mineral in the shallow aquifer sediment. Strong correlations were observed between As and Fe (R 2 = 0.57 and 0.7 for wet and dry seasons, respectively), HCO3 (R 2 = 0.65 and 0.74 for wet and dry seasons, respectively), Al (R 2 = 0.62 and 0.72 for wet and dry seasons, respectively), and a moderate correlation with DOC (R 2 = 0.39 and 0.48 for wet and dry seasons, respectively) in aquifer groundwater (<80-m depth). Based on our findings, it can be concluded that mobilization of As is due to the organic carbon instigated dissolution of Fe–Al oxyhydroxide mineral in shallow aquifer. Villagers who used to utilize this contaminated groundwater for drinking were identified to be affected with different skin complications subsequently.
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