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g the Structure of Bacteriogenic Uranium Oxides Jonathan Stahlman, Carnegie Mellon University John Bargar, Stanford Linear Accelerator Center Eleanor Schofield, Stanford Linear Accelerator Center

Characterizing the Structure of Bacteriogenic Uranium Oxides Jonathan Stahlman, Carnegie Mellon University John Bargar, Stanford Linear Accelerator Center

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Characterizing the Structure of Bacteriogenic Uranium Oxides Jonathan Stahlman, Carnegie Mellon University John Bargar, Stanford Linear Accelerator Center Eleanor Schofield, Stanford Linear Accelerator Center Slide 2 Outline Motivation Overall project This summers work Final results Slide 3 A BIG Problem Our Cold War Legacy: 1.7 trillion gallons of contaminated groundwater 40 million m 3 of contaminated soils 3 million m 3 of buried waste Contaminants: radionuclides, metals, hydrocarbons How do we manage these threats? Slide 4 One Possible Solution U(VI) Uranium - green ; Oxygen - red Shewanella oneidensis MR-1 2 e - O2O2 Nanoparticulate UO 2 Slide 5 Incorporation of other cations present in groundwater into the UO 2 structure will result in a more stable crystalline structure Hypothesis CaMgMn We will look at: Slide 6 A Structured Approach Ecole Polytechnique Fdrale de Lausanne (EPFL) Sample preparation Washington University in St. Louis Dissolution studies Stanford Synchrotron Radiation Laboratory Structural studies (EXAFS, WAXS) Slide 7 This Summers Work Wide angle x-ray scattering (WAXS) to examine lattice contraction Experimental Setup Compton Subtraction Background Subtraction Le Bail Fitting Results a Slide 8 Wide Angle X-ray Scattering Challenges: Wet Samples Radioactive Concerns Anaerobic Conditions Slide 9 Raw Data Slide 10 Compton Subtraction Compton - inelastically scattered x-rays Can be easily separated at high angle due to difference in energy Not true at lower angles 2 = 120 2 = 10 Slide 11 Compton Fits 2 = 1202 = 10 Slide 12 Background Subtraction XRD-BS: Subtract the capillary reflections Correct for absorption in the sample Slide 13 Le Bail Fitting A derivative of the Rietveld Refinement Used to extract the lattice constant Parameters: Space Group, Particle Size, Background, Lattice Constant Slide 14 Magnesium Results Undoped Sample: 5.4307 .0016 10 mM Mg Doped Sample: 5.4405 .0045 Sample pH: 8.0 Cleaning Method: NaOH Slide 15 Calcium Results Sample pH: 6.0 Cleaning Method: NaOH Undoped Sample: 5.4437 .0029 10 mM Ca Doped Sample: 5.4353 .0022 Slide 16 Manganese Results Sample pH: 6.3 Cleaning Method: NaOH Undoped Sample: 5.4331 .0016 Mn Doped Samples:.1 mM : 5.3956 .0061 1 mM : 5.4387 .0016 5 mM : 5.4018 .0022 Slide 17 Cleaning Method Results Cleanin g Method NoneNaOHLyo pH = 8 5.4753 .0025 5.4307 .0016 5.4702 .0016 pH = 6.3 - 5.4331 .0016 5.4643 .0017 pH = 6 - 5.4437 .0029 - No Dopants Added Slide 18 Conclusions Possible lattice contraction in Mn samples NaOH cleaning process is affecting the structure of bacteriogenic UO 2 Future Work: Rietveld Refinement for more structural information Possibly design new cleaning method Slide 19 Acknowledgments Funding: Department of Energy, SULI Software: Sam Webb: XRD-BS A.C. Larson and R.B. Von Dreele: GSAS B. H. Toby: EXPGUI Nita Dragoe: Powder 4 Other: Apurva Mehta John Bargar and Eleanor Schofield Slide 20 Summary Long term sequestration of bacteriogenic UO 2 depends on incorporation of cations WAXS provides structural information about bacteriogenic UO2 samples Le Bail fitting reveals: Possible lattice contraction for Mn doped sample NaOH cleaning method causing lattice contraction