Aquifers Crystallography Chemistry Calcite Arsenic Dissolution Geochemistry Groundwater Groundwater geochemistry Hydrogeology Iron compounds Iron ores Vietnam Groundwater resources Southeast Asia Oxyhydroxides
Issue Date:
2008
Publisher:
Applied Geochemistry
Citation:
Volume: 23, Issue: 11, Page : 3143-3154
Abstract:
The spatial variability of As concentrations in aquifers of the Red River Delta, Vietnam, was
studied in the vicinity of Hanoi. Two sites, only 700 m apart but with very different As concentrations in
groundwater (site L: <10 ?g/L vs. site H: 170-600 ?g/L) in the 20-50 m depth range, were characterized with
respect to sediment geochemistry and mineralogy as well as hydrochemistry. Sequential extractions of the
sediment were carried out in order to understand why As is released to groundwater at one site and not the
other. No major differences were observed in the bulk mineralogy and geochemistry of the sediment, with
the exception of the redox state of Fe oxyhydroxides inferred from sediment colour and diffuse spectral
reflectance. At site H most of the As in the sediment was adsorbed to grey sands of mixed Fe(II/III) valence
whereas at site L As was more strongly bound to orange-brown Fe(III) oxides. Higher dissolved Fe and low
dissolved S concentrations in groundwater at site H (?14 mg Fe/L, <0.3 mg S/L) suggest more strongly
reducing conditions compared to site L (1-2 mg Fe/L, <3.8 mg S/L). High concentrations of NH4
+ (?10
mg/L), HCO3
- (500 mg/L) and dissolved P (600 mg/L), in addition to elevated As at site H are consistent
with a release coupled to microbially induced reductive dissolution of Fe oxyhydroxides. Other processes
such as precipitation of siderite and vivianite, which are strongly supersaturated at site H, or the formation of
amorphous Fe(II)/As(III) phases and Fe sulfides, may also influence the partitioning of As between
groundwater and aquifer sands. The origin of the redox contrast between the two sites is presently unclear.
Peat was observed at site L, but it was embedded within a thick clayey silt layer. At site H, instead, organic
rich layers were only separated from the underlying aquifer by thin silt layers. Leaching of organic matter
from this source could cause reducing conditions and therefore potentially be related to particularly high
concentrations of dissolved NH4
+, HCO3
-, P and DOC in the portion of the aquifer where groundwater As
concentrations are also elevated. ?? 2008 Elsevier Ltd. All rights reserved.