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Paper No. 10
Presentation Time: 10:35 AM

REGIONAL TO LOCAL-SCALE EXTENT AND CONTROLS ON EXISTENCE OF DEEPER GROUNDWATER ARSENIC IN WESTERN PARTS OF BENGAL BASIN


MUKHERJEE, Abhijit, Department of Geology and Geophysics, Indian Institute of Technology (IIT), Kharagpur, 721302, India, FRYAR, Alan E., Earth & Environmental Sciences, University of Kentucky, 101 Slone Building, Lexington, KY 40506-0053 and BHATTACHARYA, Prosun, KTH-International Groundwater Arsenic Research Group, Department of Land and Water Resources Engineering, Royal Institute of Technology (KTH), Teknikringen 76, Stockholm, SE-10044, Sweden, alan.fryar@uky.edu

In the western parts of the Bengal basin [West Bengal (WB) state in India], >40 million residents use groundwater from shallow, fluvial aquifers in which elevated dissolved arsenic (As) has been detected. The generalization that As contamination is largely restricted to <100 m depth and deeper aquifers are safe is not universally accurate in the Bengal basin. As concentrations >10 ppb have been observed up to 250 m depth in WB, with ~60% of deep wells (~80% north of 22.75 °N) having elevated As. The reason is probably a combined result of hydrostratigraphy and sediment and water chemistry, reflecting differences in geologic evolution at the sub-basinal scale (cratonic stable shelf [WB] versus foreland foredeep [Bangladesh]), along with different land use in terms of divergent starting dates and types of irrigation in India and Bangladesh.

North of ~24 °N in WB, potable groundwater is only available to a depth of ~80 m; below this is a regional-scale, thick clay layer. From 24.5 °N–22.75 °N, a semi-confined sand aquifer provides vertical hydraulic continuity from near land surface to a depth of 300 m (thickening southward). This is inconsistent with inferences elsewhere of an effective, basin-wide, vertically anisotropic barrier (formed by intermediate-depth, thick clay layers) between As-rich, shallow aquifers and safe, deep aquifers. No regionally extensive, oxidized stratum could be mapped to a depth of 300 m in WB. Water chemistry (major and trace solutes and redox parameters from >120 wells) and sediment chemistry (sequential extraction of solid-phase As from multiple boreholes, to 232 m depth) indicate that reducing conditions conducive to As mobilization can occur at >200 m depth.

A regional, heterogeneous, vertically and horizontally anisotropic groundwater flow model, which incorporates observed shallow and deep pumping, shows that As-laden groundwater could have moved to >150 m depth in the semi-confined aquifer without an effective hydraulic barrier since the early 1970s. This is substantiated by depth profiles of environmental tracers (18O, Cl, and 3H) at a modeled, local-scale study site in WB. Deep pumping for irrigation and public supply at >100 m depth is pervasive in WB, with >2000 large diameter wells installed since the early 1970s, in contrast to infrequent deep groundwater use in Bangladesh.

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