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Published on: June 21, 2015
Geochemical control on uranium(IV) mobility in a mining-impacted wetland
Yuheng Wang1, Alexandre Bagnoud, Elena Suvorova
1Ecole Polytechnique Fédérale de Lausanne (EPFL) - Environmental Microbiology Laboratory (EML) EPFL-ENAC-IIE-EML, Station 6, CH-1015 Lausanne, Switzerland.
Wetlands can immobilize uranium (U). In clay-poor areas, U binds to soil organic matter, limiting its mobility. This contrasts with clay-rich zones where U mobility is higher due to associations with iron and organic colloids.
Area of Science:
- Environmental Science
- Geochemistry
- Environmental Chemistry
Background:
- Wetlands act as natural sinks for uranium (U) and trace elements.
- Previous studies identified labile noncrystalline U(IV) species bound to Al-P-Fe-Si aggregates in clay-rich wetland soils.
- Uranium mobility in porewater was linked to its association with Fe(II) and organic matter colloids.
Purpose of the Study:
- To investigate uranium speciation and mobility in a clay-poor wetland location.
- To compare uranium behavior in clay-poor versus clay-rich wetland environments.
- To elucidate factors controlling uranium immobilization in wetlands.
Main Methods:
- Field sampling in a mining-impacted wetland in France.
- Analysis of uranium speciation in soil and porewater.
- Assessment of microbial sulfate reduction and iron speciation.
Main Results:
- A different noncrystalline U(IV) species, bound to soil organic matter, dominates in clay-poor locations.
- Clay-poor areas exhibit abundant sulfate and microbial sulfate reduction, leading to pyrite precipitation.
- Lower Fe(II) concentrations in porewater of clay-poor zones result in significantly reduced uranium porewater concentrations and mobility.
- Soil-associated uranium constitutes over 99% of total uranium in both studied locations.
Conclusions:
- Low uranium mobility in clay-poor wetland locations is attributed to limited Fe(II) association with organic matter colloids in porewater.
- Alternatively, higher stability of the noncrystalline U(IV) species bound to soil organic matter contributes to uranium immobilization.
- Wetland characteristics, particularly clay content and microbial activity, significantly influence uranium speciation and mobility.
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