4.8 Article

Uranium Binding Mechanisms of the Acid-Tolerant Fungus Coniochaeta fodinicola

Journal

ENVIRONMENTAL SCIENCE & TECHNOLOGY
Volume 49, Issue 14, Pages 8487-8496

Publisher

AMER CHEMICAL SOC
DOI: 10.1021/acs.est.5b01342

Keywords

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Funding

  1. Australian Research Council Linkage Project [LP100200792]
  2. ERA
  3. ANSTO Minerals
  4. Australian Research Council Future Fellowship [FT110100067]
  5. Australian Research Council [LP100200792, FT110100067] Funding Source: Australian Research Council

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The uptake and binding of uranium [as (UO2)(2+)] by a moderately acidophilic fungus, Coniochaeta fodinicola, recently isolated from a uranium mine site, is examined in this work in order to better understand the potential impact of organisms such as this on uranium sequestration in hydrometallurgical systems. Our results show that the viability of the fungal biomass is critical to their capacity to remove uranium from solution. Indeed, live biomass (viable cells based on vital staining) were capable of removing similar to 16 mg U/g dry weight in contrast with dead biomass (autoclaved) which removed similar to 45 mg U/g dry weight after 2 h. Furthermore, the uranium binds with different strength, with a fraction ranging from similar to 20-50% being easily leached from the exposed biomass by a 10 min acid wash. Results from X-ray absorption spectroscopy measurements show that the strength of uranium binding is strongly influenced by cell viability, with live cells showing a more well-ordered uranium bonding environment, while the distance to carbon or phosphorus second neighbors is similar in all samples. When coupled with time-resolved laser fluorescence and Fourier transformed infrared measurements, the importance of organic acids, phosphates, and polysaccharides, likely released with fungal cell death, appear to be the primary determinants of uranium binding in this system. These results provide an important progression to our understanding with regard to uranium sequestration in hydrometallurgical applications with implications to the unwanted retention of uranium in biofilms and/or its mobility in a remediation context.

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