Jm. Mcarthur et al., Arsenic in groundwater: Testing pollution mechanisms for sedimentary aquifers in Bangladesh, WATER RES R, 37(1), 2001, pp. 109-117
In the deltaic plain of the Ganges-Meghna-Brahmaputra Rivers, arsenic conce
ntrations in groundwater commonly exceed regulatory limits (>50 mug L-1) be
cause FeOOH is microbially reduced and releases its sorbed load of arsenic
to groundwater. Neither pyrite oxidation nor competitive exchange with fert
ilizer phosphate contribute to arsenic pollution. The most intense reductio
n and so severest pollution is driven by microbial degradation of buried de
posits of peat. Concentrations of ammonium up to 23 mg L-1 come from microb
ial fermentation of buried peat and organic waste in latrines. Concentratio
ns of phosphorus of up to 5 mg L(-)1 come from the release of sorbed phosph
orus when FeOOH is reductively dissolved and from degradation of peat and o
rganic waste from latrines. Calcium and barium in groundwater come from dis
solution of detrital land possibly pedogenic) carbonate, while magnesium is
supplied by both carbonate dissolution and weathering of mica. The Sr-87/S
r-86 values of dissolved strontium define a two-component mixing trend betw
een monsoonal rainfall (0.711 +/- 0.001) and detrital carbonate (<0.735).