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Understanding biological uranium reduction Sherilee Palm Energy Postgraduate Conference 2013 Supervisor: Prof E. van Heerden Co-supervisors: Errol Cason Dr. D. Opperman
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Introduction Microbe – metal interactions: Systems Bioaccumulation Biomineralization Biosorption Bioreduction (Beliaev et al., 2001)
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Introduction (Vaughan and Lloyd, 2011)
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Aims Assess the microbial diversity of uranium and thorium contaminated water. Use metal-reducing bacteria as biocatalysts for uranium and thorium bioreduction. Use known genomes of metal reducers to elucidate metabolic capabilities.
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Diversity
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To understand how a biological process occurs, two routes can be followed: Let the microorganism do the work Assess the genome of the microorganism to determine if it has the correct tools to do the work.
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Uranium reduction U (IV)U (VI) –Mobile –Soluble –Toxic Mutagen & carcinogenic U(IV) –Immobile –Insoluble –Less toxic (Payne, 2005; Cason et al., 2012; Abdelouas et al., 2000)
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Enzymatic U(VI) reduction The Lovley Model: (Lovley et al., 1993; Cason et al., 2012 ) Peptide ABC transporter, peptide-binding protein
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External electron transport systems (Valocchi, 2011)
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Conclusions Microbial encounters with metals in the environment are inevitable, consequently microbes have developed defence mechanisms against metal toxicity. A mechanistic understanding of uranium (and thorium) bioreduction/biosorption could aid in devising an effective and economically feasible bioremediation process for the removal/separation of these metals.
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Acknowledgements University if the Free State Prof Esta van Heerden Extreme biochemistry NRF (SANHARP)
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T: +27(0)51 401 9039 | malekemm@ufs.ac.za Thank you Dankie ¡gracias شكرا Děkuji Danke Grazie gratias ago vos Ke a leboha T: +27 (0)51 401 9897palmsm@ufs4life.ac.za
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