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December 12, 2007 A Macroscopic and Spectroscopic Study on Arsenate Uptake by CalciteV.G. Alexandratos1,3, E.J. Elzinga2,3 and R.J. Reeder3 Combined use of EXAFS and
Uptake mechanisms on mineral surfaces, including adsorption, coprecipitation and precipitation, influence the mobility and bioavailability of chemical species in natural systems. Arsenic (As) is a toxic metalloid that can be introduced into the environment through natural sources (e.g. mineral weathering, geothermal processes) and/or through anthropogenic activities (e.g. industry, mining, agriculture). In oxidized environments As is mainly present in the 5+ oxidation state as arsenate (AsO43-). Much research has focused on the uptake of As species by various common minerals, and specifically for As(V) it has been shown that formation of a strongly bound surface adsorption complex is a dominant mechanism over a range of environmentally relevant conditions (e.g. pH, ionic strength, reaction time). Calcite, an abundant and reactive mineral component of soil and aquifer systems, has been shown to be an effective sorbent of metals and oxyanions. Prior studies have shown that metal uptake is subject to strong surface site preferences that may control the partitioning of dissolved species between the aqueous and solid phase. In combination with batch uptake experiments on calcite we investigated AsO43- uptake mechanisms, including adsorption and
coprecipitation, using As K-edge x-ray absorption spectroscopy and micro-x-ray fluorescence mapping (
The critical factor that makes it possible to identify surface site preferences for As(V) uptake is that spiral growth on the
calcite (1014) surface results in the formation of two characteristic non-equivalent pairs of vicinal surfaces, denoted as "+"
and "–," that differ in the structure of surface sites in their growth steps (Figure 1c). The
To gain insight to As(V) sorption mechanisms at the calcite surface, we collected As K-edge EXAFS data on As(V)-sorbed calcite in wet paste samples. Fitting results confirm formation of a tetrahedral inner-sphere surface complex with two separate Ca shells at distances of 3.4 and 3.6 Å. Although it is not possible to distinguish differences in sorption geometry between different sites in the batch sorption samples used for EXAFS, we can constrain aspects of the dominant binding mode. The presence of the two Ca shells indicates either the co-existence of more than one As(V) surface complex or a dominant coordination as a bidentate complex in steps or a tridentate complex in kink sites (Figure 2 a-d). These conclusions are consistent with the strong binding that has been observed in batch studies, and provides information for further modeling of surface interactions of As species with calcite surfaces. BEAMLINES FUNDING PUBLICATION FOR MORE INFORMATION |