Arsenic sequestration by ferric iron plaque on cattail roots
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作者:
Blute, NK
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MIT, Ralph M Parsons Lab, Dept Civil & Environm Engn, Cambridge, MA 02139 USAMIT, Ralph M Parsons Lab, Dept Civil & Environm Engn, Cambridge, MA 02139 USA
Blute, NK
[1
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Brabander, DJ
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机构:MIT, Ralph M Parsons Lab, Dept Civil & Environm Engn, Cambridge, MA 02139 USA
Brabander, DJ
Hemond, HF
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机构:MIT, Ralph M Parsons Lab, Dept Civil & Environm Engn, Cambridge, MA 02139 USA
Hemond, HF
Sutton, SR
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机构:MIT, Ralph M Parsons Lab, Dept Civil & Environm Engn, Cambridge, MA 02139 USA
Sutton, SR
Newville, MG
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机构:MIT, Ralph M Parsons Lab, Dept Civil & Environm Engn, Cambridge, MA 02139 USA
Newville, MG
Rivers, ML
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机构:MIT, Ralph M Parsons Lab, Dept Civil & Environm Engn, Cambridge, MA 02139 USA
Rivers, ML
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[1] MIT, Ralph M Parsons Lab, Dept Civil & Environm Engn, Cambridge, MA 02139 USA
[2] Univ Chicago, Dept Geophys Sci, Chicago, IL 60637 USA
[3] Univ Chicago, Consortium Adv Radiat Sources, Chicago, IL 60637 USA
Typha latifolia (cattail) sequesters arsenic within predominantly ferric iron root coatings, thus decreasing mobility of this toxic element in wetland sediments. Element-specific XRF microtomographic imaging illustrated a high spatial correlation between iron and arsenic in root plaques, with little arsenic in the interior of the roots. XANES analyses demonstrated that the plaque was predominantly ferric iron and contained approximately 20% As(III) and 80% As(V), which is significant because the two oxidation states form species that differ in toxicity and mobility. For the first time, spatial distribution maps of As oxidation states were developed, indicating that As(III) and As(V) are both fairly heterogeneous throughout the plaque. Chemical extractions showed that As was strongly adsorbed in the plaque rather than coprecipitated. Iron and arsenic concentrations ranged from 0.03 to 0.8 g Fe g(-1) wet plaque and 30 to 1200 mug As g(-1) wet plaque, consistent with a mechanism of As adsorption onto Fe(III) oxyhydroxide plaque. Because this mechanism decreases the concentrations of both As(III) and As(V) in groundwater, we propose that disruption of vegetation could increase the concentrations of mobile arsenic.
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MIT, Dept Civil & Environm Engn, Ralph M Parsons Lab, Cambridge, MA 02139 USAMIT, Dept Civil & Environm Engn, Ralph M Parsons Lab, Cambridge, MA 02139 USA
Brabander, DJ
Keon, N
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MIT, Dept Civil & Environm Engn, Ralph M Parsons Lab, Cambridge, MA 02139 USAMIT, Dept Civil & Environm Engn, Ralph M Parsons Lab, Cambridge, MA 02139 USA
Keon, N
Stanley, RHR
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MIT, Dept Civil & Environm Engn, Ralph M Parsons Lab, Cambridge, MA 02139 USAMIT, Dept Civil & Environm Engn, Ralph M Parsons Lab, Cambridge, MA 02139 USA
Stanley, RHR
Hemond, HF
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MIT, Dept Civil & Environm Engn, Ralph M Parsons Lab, Cambridge, MA 02139 USAMIT, Dept Civil & Environm Engn, Ralph M Parsons Lab, Cambridge, MA 02139 USA
机构:
MIT, Dept Civil & Environm Engn, Ralph M Parsons Lab, Cambridge, MA 02139 USAMIT, Dept Civil & Environm Engn, Ralph M Parsons Lab, Cambridge, MA 02139 USA
Brabander, DJ
Keon, N
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MIT, Dept Civil & Environm Engn, Ralph M Parsons Lab, Cambridge, MA 02139 USAMIT, Dept Civil & Environm Engn, Ralph M Parsons Lab, Cambridge, MA 02139 USA
Keon, N
Stanley, RHR
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MIT, Dept Civil & Environm Engn, Ralph M Parsons Lab, Cambridge, MA 02139 USAMIT, Dept Civil & Environm Engn, Ralph M Parsons Lab, Cambridge, MA 02139 USA
Stanley, RHR
Hemond, HF
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MIT, Dept Civil & Environm Engn, Ralph M Parsons Lab, Cambridge, MA 02139 USAMIT, Dept Civil & Environm Engn, Ralph M Parsons Lab, Cambridge, MA 02139 USA