Groundwater geochemistry and its implications for arsenic mobilization in shallow aquifers of the Hetao Basin, Inner Mongolia.
Arsenic concentrations in shallow groundwaters from the Hetao Basin of Inner Mongolia range between 0.6 and 572 microg/L. High As groundwaters generally occur in the shallow alluvial-lacustrine aquifers, which are mainly composed of black (or dark grey) fine sands in a reducing environment. They are characterized by high concentrations of dissolved Fe, Mn, HCO(3)(-), P and S(2-), and low concentrations of NO(3)(-) and SO(4)(2-). Low SO(4)(2-) coupled with high S(2-) suggests that SO(4)(2-) reduction has been an active process. In the reducing groundwaters, inorganic As(III) accounts for around 75% of total dissolved As. Total As contents in the sediments from three representative boreholes are observed to be 7.3-73.3 mg/kg (average of 18.9 mg/kg). The total As is mildly-strongly correlated with total Fe and total Mn, while a quite weak correlation exists between total As and total S, suggesting that the As is associated with Fe-Mn oxides, rather than sulfides in the sediments. It is found in the sequential extraction that chemically active As is mainly bound to Fe-Mn oxides, up to 3500 microg/kg. The mobilization of As under reducing conditions is believed to include reductive dissolution of Fe-Mn oxides and reduction of adsorbed As. Although exchangeable As is labile and very vulnerable to hydrogeochemical condition, the contribution is relatively limited due to the low concentrations. The competition between As and other anions (such as HPO(4)(2-)) for binding sites on Fe-Mn oxides may also give rise to the release of As into groundwater. Slow groundwater movement helps accumulation of the released As in the groundwaters.
Guo
Huaming
H
School of Water Resources and Environment, China University of Geosciences, Beijing 100083, People's Republic of China. hmguo@cugb.edu.cn
Yang
Suzhen
S
Tang
Xiaohui
X
Li
Yuan
Y
Shen
Zhaoli
Z
D001151:Arsenic / Q000032:analysis*; D001639:Bicarbonates / Q000032:analysis; D002681:China; D002712:Chlorides / Q000032:analysis; D004784:Environmental Monitoring; D005461:Fluorine / Q000032:analysis; D019015:Geologic Sediments / Q000032:analysis; D008670:Metals / Q000032:analysis; D009566:Nitrates / Q000032:analysis; D010087:Oxides / Q000032:analysis; D010758:Phosphorus / Q000032:analysis; D013431:Sulfates / Q000032:analysis; D013455:Sulfur / Q000032:analysis; D014874:Water Pollutants, Chemical / Q000032:analysis*; D014881:Water Supply / Q000032:analysis*
D001639:Bicarbonates; D002712:Chlorides; D008670:Metals; D009566:Nitrates; D010087:Oxides; D013431:Sulfates; D014874:Water Pollutants, Chemical; D010758:Phosphorus; D005461:Fluorine; D013455:Sulfur; D001151:Arsenic