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- Exported organic carbon promotes reducing conditions and redox cycling in oxic aquifers
- Soil organic matter controls Pb release during redox cycles in floodplain soils
- Spatial and Compositional Heterogeneities Control Zn Retention Mechanisms in a Simulated Aquifer
- Calcium-Uranyl-Carbonato Species Kinetically Limit U(VI) Reduction by Fe(II) and Result in U(V)-bearing Ferrihydrite
- Diverse Ammonia-Oxidizing Archaea Dominate Subsurface Nitrifying Communities in Semi-Arid Floodplains
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- Complexation Organic Matter Controls Uranium Mobility Anoxic Sediments
- FES-Nanoclusters can mobilize Fe and S from sediment to the groundwater
- Hexavalent uranium storage mechanisms in wet-dry cycled sediments at contaminated DOE sites in the Western U.S.
- Redox-Interfaces can Produce Toxic Arsenic Levels Groundwater...
- Sorption to Organic Matter Controls Uranium Mobility
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- Long-Term in Situ Oxidation of Biogenic Uraninite in an Alluvial Aquifer: Impact of Dissolved Oxygen and Calcium
- U Release from NRZ sediments is inhibited by Transport and Geochemistry
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Ferrihydrite Sulfidation Promotes FeS Nanocluster Formation
The Science
Nanometer to micrometer sized mineral particles (often associated with organic carbon and often referred to as colloids) that remain suspended in water can play major roles in mediating the mobility of nutrients, metals and radionuclides in groundwater. Yet, the factors controlling their occurrence and stability are poorly understood. The reaction of common soil Fe(III) oxyhydroxides with dissolved HS- has been proposed as a pathway by which sulfidic nanoparticles can be naturally generated in groundwater. In this study, we confirmed that this process can form stable iron monosulfide nanoclusters. (Clusters are defined here as precursors of nanoparticles) The rate of sulfidation, ionic strength of the groundwater, and abundance of organic compounds, were found to control the stability of FeS nanocluster suspensions generated from ferrihydrite sulfidation. Moreover, we provided a conceptual model for predicting the conditions under which sulfidation of ferrihydrite will generate FeS nanoclusters.
The Impact
In low-salinity, low-sulfate groundwater systems, common in many floodplains, sulfidation of ferrihydrite will generate FeS nanoclusters that will remain suspended and can be transported by groundwater. These materials can sorb metal micronutrients (e.g., Mn) and contaminants (e.g., Zn), allowing them to be mobilized to surface waters or to reactive zones in the aquifer where they may be utilized by microorganisms or accumulate as contaminant loads. These observations highlight the potential for sulfidic conditions to mobilize trace metals and promote their biogeochemical cycling. These conclusions place a large asterisk on the conventional view that sulfidic conditions generally stabilize metals through precipitation reactions.
Summary
We have used synchrotron-based EXAFS spectroscopy, transmission electron microscopy, Fourier-transform ion-cyclotron-resonance mass spectrometry, and aqueous measurements to determine the stability and molecular structure of nanoclusters generated by sulfidation of ferrihydrite and to identity the composition of natural organic carbon compounds associated with them. This research shows that sulfidation of ferrihydrite generates nm-scale aqueous FeS clusters. Their tendency to condense into nanoparticles, aggregate, and settle, was directly related to the sulfide/Fe ratio. At sulfide/Fe ratios ≤0.5, FeS nanoclusters and larger nanoparticles remained in suspension for up to several months. At sulfide/Fe ratios >0.5, sulfidation reaction rates were rapid and FeS nanocluster aggregation was accelerated. The presence of organic compounds increased the time of suspension of FeS nanoclusters, whereas increased ionic strength inhibited the generation of FeS nanoclusters.
FeS nanoclusters are responsible for electron transfer in many biogeochemical pathways. Thus, suspended FeS nanoclusters could function as electron shuttles, influencing geochemical processes and heterotrophic microbial activity in aquifers. Moreover, FeS nanoclusters can directly bind nutrients and contaminants via sorption reactions and contribute to their transport in (sub)surface waters. This statement is corroborated by numerous previous studies proposing that contaminant mobility in groundwater can be directly associated with FeS mobility in the aqueous fraction.
Contacts (BER PM)
Amy Swain
DOE Office of Biological and Environmental Research, Climate and Environmental Sciences Division
Amy.Swain@science.doe.gov
(PI contact)
John Bargar
SLAC National Accelerator Laboratory, Stanford Synchrotron Radiation Lightsource
Bargar@slac.stanford.edu
Funding
Funding was provided by the DOE Office of Biological and Environmental Research, Subsurface Biogeochemistry Research (SBR) activity to the SLAC SFA program under contract DE-AC02-76SF00515 to SLAC. Research was performed at SSRL, a national user facility supported by the U.S. DOE, Office of Basic Energy Sciences. A portion of the research was performed using EMSL (grid.436923.9), a Science User Facility sponsored by the U.S. DOE, Office of Biological and Environmental Research.
Publications
Noël, V., Kumar, N., Boye, K., Barragan, L., Lezama-Pacheco, J., Chu, R., Tolic, N., Gordon E. Brown Jr., G.E, Bargar, J.R. (2020) FeS Colloids – Formation and Mobilization Pathways in Natural Waters. Environmental Science Nano., Accepted Manuscript
Related Links
DOI: 10.1039/C9EN01427F
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