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Migration of As, and H/He ages, in groundwater from West Bengal: Implications for monitoring
Authors:J.M. McArthur  D.M. Banerjee  S. Klump  R. Kipfer
Affiliation:a Department of Earth Sciences, University College London, Gower Street, London WC1E 6BT, UK
b Department of Geology, University of Delhi, Delhi 110 007, India
c Department of Geology and Geophysics, Indian Institute of Technology, Kharagpur, West Bengal 721 302, India
d Entec UK Ltd, Trinity House, Cambridge Business Park, Cowley Road, Cambridge, CB4 0WZ, UK
e Eawag, Swiss federal Institute of Aquatic Science and Technology, Department of Water Resources and Drinking Water, 8600 Dübendorf, Switzerland and Isotope Geology, ETH, Zurich, 8092 Zurich, Switzerland
f Dept. Geographical and Geological Sciences, Kingston University, Penrhyn Road, Kingston upon Thames KT1 2EE, UK
g Present address Centre for Environmental Policy, Imperial College London, Silwood Park Campus, Ascot SL5 7PY, UK
Abstract:From 2002 to 2010 inclusive we monitored concentrations of arsenic (As) and major ions (Ca, Mg, Sr, Na, K, Fe, Mn, Cl, and SO4) in groundwater from 14 domestic wells and three piezometer nests in a shallow aquifer (<60 m depth), and 3 wells in a deep aquifer (>70 m depth), in southern West Bengal, India. In the deep aquifer, concentrations of As did not change over time despite increases in the concentration of Fe in two wells. The shallow aquifer occurs in two sedimentological settings: palaeo-channel and palaeo-interfluve. At the top of the shallow aquifer of the palaeo-channel, decreases in all constituent concentrations with time, and an 3H/3He age of 1.4 years, proves that the aquifer is beginning to be flushed of pollutants. In As-polluted groundwater (>50 μg/L As) tapped from deeper grey sands of the shallow, palaeo-channel, aquifer, concentrations of As were mostly stable over time, but both increases and decreases occurred with time in response to downward migration of the chemically-stratified water column. In groundwater tapped from Pleistocene brown sands, the concentration of As remained either low and stable (<2 μg/L As), or increased at rates up to 34 μg/L per year. The increases were caused by the flow of As-rich groundwater either downward into brown sand at the base of palaeo-channels, or laterally into a confined, unpolluted, palaeo-interfluvial, aquifer of brown sand that lies regionally beneath a palaeosol.Under the present pumping regime, the prognosis for As-pollution in the shallow aquifer is complex. Wells in brown sand may become polluted over timescales of as little as 2 years, whilst some wells tapping As-polluted groundwater from grey sand will become fit for potable use (<50 μg/L) within a few decades. The evidence of flushing, and of declining As in some of the groundwater from palaeo-channels, which are conduits for recharge of the confined, As-free, palaeo-interfluve aquifer, and probably also the deeper aquifer, offers hopes that the spread of As-pollution will be limited.
Keywords:Arsenic   As   Pollution   Bengal basin   Groundwater   West Bengal   Flushing   Dating   3H/3He   Tritium
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