Abstract:Accidental release of plutonium (Pu) from storage facilities in the subsurface environment is a concern for the safety of human beings and the environment. Given the complexity of the subsurface environment and multivalent state of Pu, we developed a quantitative biogeochemical framework for bioremediation of Pu(V)O(2) (+) in the subsurface environment. We implemented the framework in the biogeochemical model CCBATCH by expanding its chemical equilibrium for aqueous complexati… Show more
“…Due to high ionic charge, it can undergo hydrolysis and convert to a polymeric form at pH > 2. Information is limited on the influence of microbes on the solubility of Pu (Deo & Rittmann, 2012;Deo et al, 2011). The chemical speciation of Pu can be influenced by the soil's pH, redox conditions, organic content, mineralogy, and microbial activities (Francis, 2007).…”
Section: Plutonium Biotransformation and Remediation Studiesmentioning
“…Due to high ionic charge, it can undergo hydrolysis and convert to a polymeric form at pH > 2. Information is limited on the influence of microbes on the solubility of Pu (Deo & Rittmann, 2012;Deo et al, 2011). The chemical speciation of Pu can be influenced by the soil's pH, redox conditions, organic content, mineralogy, and microbial activities (Francis, 2007).…”
Section: Plutonium Biotransformation and Remediation Studiesmentioning
“…Limitations to microbial reduction of metals and radionuclide also arise from low pH environments that must be neutralized to support growth of sulfate-and metalreducing communities [163,169,170]. Additionally, microbial reduction in mixed waste environments must be carefully considered so as to minimize contaminant migration of elements such as As and Pu that demonstrate greater mobility in their reduced valence states [171,172].…”
Section: Challenges For In Situ Immobilization Of Metals and Radionucmentioning
confidence: 99%
“…Furthermore, contaminated sites that are characterized by acidic to circumneutral porewater pH represent environments that can support stable mineral formation (Figures 2(a) and 2(b)), provided that carbonates are not present in significant concentrations (i.e.,P CO 2 < 10 −3.5 atm) [176,177]. Interestingly, investigations of microbial reduction of Cr, Np, Pu, and U have been shown to support subsequent phosphate precipitation reactions via thermodynamic modeling, chromatographic separation of actinides based on valence state, and X-ray analytical methods [154,155,172,178,179]. Unlike U, that is capable of forming phosphate minerals in both hexavalent and tetravalent states [50,179], the reduction of Cr, Np, and Pu is initially required for these contaminants to participate in phosphate precipitation reactions [154,155,172,178].…”
Section: Challenges For In Situ Immobilization Of Metals and Radionucmentioning
confidence: 99%
“…Interestingly, investigations of microbial reduction of Cr, Np, Pu, and U have been shown to support subsequent phosphate precipitation reactions via thermodynamic modeling, chromatographic separation of actinides based on valence state, and X-ray analytical methods [154,155,172,178,179]. Unlike U, that is capable of forming phosphate minerals in both hexavalent and tetravalent states [50,179], the reduction of Cr, Np, and Pu is initially required for these contaminants to participate in phosphate precipitation reactions [154,155,172,178]. To date, only pure culture or coculture studies have identified such coupled microbial interactions that offer an additional approach to control contaminant toxicity and mobility that are perpetuated by valence state cycling.…”
Section: Challenges For In Situ Immobilization Of Metals and Radionucmentioning
Worldwide industrialization activities create vast amounts of organic and inorganic waste streams that frequently result in significant soil and groundwater contamination. Metals and radionuclides are of particular concern due to their mobility and longterm persistence in aquatic and terrestrial environments. As the global population increases, the demand for safe, contaminantfree soil and groundwater will increase as will the need for effective and inexpensive remediation strategies. Remediation strategies that include physical and chemical methods (i.e., abiotic) or biological activities have been shown to impede the migration of radionuclide and metal contaminants within soil and groundwater. However, abiotic remediation methods are often too costly owing to the quantities and volumes of soils and/or groundwater requiring treatment. The in situ sequestration of metals and radionuclides mediated by biological activities associated with microbial phosphorus metabolism is a promising and less costly addition to our existing remediation methods. This review highlights the current strategies for abiotic and microbial phosphatemediated techniques for uranium and metal remediation.
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