Origin of As spatial heterogeneity in organic-rich by-products of riparian wetland soil oxidation using sulfur K-edge extended X-ray absorption fine structure (EXAFS)
Abstract
Extensive arsenic poisoning in drinking water has been reported in Asia,
Argentina, Chile and Mexico. The contamination can derive from reduction
processes occurring at soil near-surface and especially in riparian
wetlands. The major characteristic of these areas is that flooding induces
alternating oxidizing and reducing conditions in accordance with
the water saturation. It has been shown that under reduced conditions,
As and Fe solubilization is increased by the presence of colloidal organic
matter (OM) in soil solution. But what happens to As when the
water level decreases and subsequent soil oxidation is established ?
Samples consisting of reoxidation products (Fe-OM rich) of a riparian
soil solution are collected on PTFE plates inserted into the upper horizons
of the soil during the dry season. Geochemical analyzes showed
75% of OM, 9% of Fe and 250 mg.g-1 of As. First SEM and NanoSIMS
results indicate that As is not only associated with Fe-oxides as expected
in oxidized conditions, but also with OM and S-rich particles. Studies
demonstrated that, in peat, As (III) is as sulphide minerals or directly
bound to OM via sulfhydryl sites. However,in the oxidized precipitates,
it is unlikely that As being as sulphide minerals and the sole OM-SH
complexes cannot explain such concentration. Thereby, the presence of
As-rich OM(S) is still unsolved.
XAS (XANES and EXAFS) spectroscopy has been used to determine
the local environment of sulfur since it appeared to be a key factor in
the binding of As to OM. XAS was performed at the sulfur K-edge (Lucia
beamline, Soleil synchrotron, Saclay) on our natural samples and
several model compounds. Using XANES, sulfur could be seen in several
oxidation degrees (from -II to +VI). EXAFS spectra will then provide
information on the As-S, S-O, and perhaps on S-C bonding and
will highlight the relation between As and OM. Thereby those results
will show the ability of OM to directly or not bind As under oxidizing
conditions and therefore whether wetlands are sinks or sources to As.