Masters Degrees (Microbial, Biochemical and Food Biotechnology)
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Browsing Masters Degrees (Microbial, Biochemical and Food Biotechnology) by Author "Botes, E."
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Item Open Access Biological reduction of soluble uranium by an indigenous bacterial community(University of the Free State, 2013-07) Maleke, Mathews Maleke; Van Heerden, E.; Williams, P. J.; Botes, E.English: Uranium (U) and chromium (Cr) in groundwater are a serious public health concern due to their chemical toxicity. Even so, microorganisms have developed mechanisms which permit them to thrive under previously perceived uninhabitable conditions. A number of bacteria have been isolated from areas impacted with the soluble heavy metals, and can be exploited as bioremediation agents since they are well adapted to these metals. To date, the use of microbial mechanisms for bioremediation processes is a growing industry since it provides green and sustainable technologies. In this study, the upflow bioreactors were used as a low cost, low maintenance effective bioremediation strategy in comparison to the available methods of remediation. Two metals known to be toxic in their soluble state were treated. The first was Cr(VI) from an impacted site in Limpopo and the second was U(VI) from the Wonderfonteinspruit catchment, North West Province. The system was efficient for the removal of soluble Cr(VI) and U(VI) from the impacted water through biostimulation of indigenous bacterial communities. This system can be up scaled and employed for the remediation of impacted sites, and it will be useful especially at low levels of U(VI). Indigenous bacterial community from impacted sites have the capability to reduce Cr(VI) and U(VI) effectively over a sustainable period. The shortage of electron donor and continuous oxygen exposure in the case of U(VI) act as a limiting factor. However, in this study successful Cr(VI) and U(VI) reduction rates were increased by the addition of an electron donor to stimulate the indigenous bacterial community. Furthermore, a third upflow bioreactor showed that it is even possible with gradual increases of U(VI) concentration that U(VI) bioreduction is possible at very high levels. The influent water was spiked step wise with uranyl acetate, allowed to reach maximal U(VI) reduction/removal and then the diversity was assessed. Despite the 10 mg/l U(VI) fed to the bioreactor, the established microbial community was able to tolerate, adapt and thereby remove the U(VI) from the spiked water. Even though biofilm could not sturdily adhere to the matrix from the bioreactor, high levels of U(VI) removal could be achieved and the planktonic community maintained. No biofilm could be observed from SEM analysis from the TEM it was observed that the planktonic microbial community have an interaction with uranium. Since no U(VI) could be detected from the effluent samples, it is thus postulated the uranium in contact with the microbial cells is in another form, probably U(IV) as previously shown in this laboratory. This study allows for the understanding of the metal microbe interactions in impacted environments, the use of this biome to remediate the water in an effective, low cost and maintenance bioreactor.