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Uranium contamination is a serious concern at several sites motivating the development of novel treatment strategies such as the Geobacter-mediated reductive immobilization of uranium. However, this bioremediation strategy has not yet been optimized for the sustained uranium removal. While several reactive-transport models have been developed to represent Geobacter-mediated bioremediation of uranium, these models often lack the detailed quantitative description of the microbial process (e.g., biomass build-up in both groundwater and sediments, electron transport system, etc.) and the interaction between biogeochemical and hydrological process. In this study, a novel multi-scale model was developed by integrating our recent model on electron capacitance of Geobacter (Zhao et al., 2010) with a comprehensive simulator of coupled fluid flow, hydrologic transport, heat transfer, and biogeochemical reactions. This mechanistic reactive-transport model accurately reproduces the experimental data for the bioremediation of uranium with acetate amendment. We subsequently performed global sensitivity analysis with the reactive-transport model in order to identify the main sources of prediction uncertainty caused by synergistic effects of biological, geochemical, and hydrological processes. The proposed approach successfully captured significant contributing factors across time and space, thereby improving the structure and parameterization of the comprehensive reactive-transport model. The global sensitivity analysis also provides a potentially useful tool to evaluate uranium bioremediation strategy. The simulations suggest that under difficult environments (e.g., highly contaminated with U(VI) at a high migration rate of solutes), the efficiency of uranium removal can be improved by adding Geobacter species to the contaminated site (bioaugmentation) in conjunction with the addition of electron donor (biostimulation). The simulations also highlight the interactive effect of initial cell concentration and flow rate on U(VI) reduction.
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http://dx.doi.org/10.1002/bit.23096 | DOI Listing |
Sheng Wu Gong Cheng Xue Bao
August 2025
Key Discipline Laboratory for National Defense for Biotechnology in Uranium Mining and Hydrometallurgy, University of South China, Hengyang 421001, Hunan, China.
MR-1, a Gram-negative bacterium with a significant role in the adsorption and reduction of uranium in wastewater and a quorum-sensing effect, can be used to remove uranium from wastewater. Exogenous signaling molecules (acyl-homoserine lactones, AHLs) can be added to induce the quorum sensing behavior for rapid biofilm formation, thereby improving the removal efficiency of this bacterium for uranium. Extracellular polymeric substances (EPS), as the significant components of biofilm, play a key role in biofilm formation.
View Article and Find Full Text PDFJ Hazard Mater
August 2025
Department of Environmental and Resource Engineering, Technical University of Denmark, Bygningstorvet, Bygning 115, Kgs Lyngby 2800, Denmark. Electronic address:
Efficient and eco-friendly purification of uranium-bearing wastewater is essential for the safety of the water ecosystem and sustainable development of the nuclear energy industry. Although bioelectrochemical systems show great prospect for uranium bioremediation, the uranium removal efficiency is often limited by the ineffective quality of biofilm formation and unsatisfactory electron transfer. Here we propose a rapid self-assembled biofilm formation strategy to construct a sulfate-reducing bacteria-carbon cloth biohybrid cathode (CF-PQ7) modified with cotton-derived carbon fibers for the simultaneous removal of uranium and sulfate.
View Article and Find Full Text PDFJ Hazard Mater
September 2025
College of Water Sciences, Beijing Normal University, Beijing 100875, China; Engineering Research Center for Groundwater Pollution Control and Remediation Ministry of Education, College of Water Sciences, Beijing Normal University, Beijing 100875, China. Electronic address:
Biochar enhances microbial extracellular electron transfer (EET) by acting as an electron mediator. However, the role of persistent free radicals (PFRs) in biochar facilitating EET, and strategies to enhance their function through chemical modification, remain underexplored. In this study, the mechanisms by which oxygen-centred PFRs in chemically modified biochar affected U(VI) reduction through the component Desulfovibrio vulgaris UR1 were investigated.
View Article and Find Full Text PDFJ Hazard Mater
September 2025
School of Life Science, Agriculture and Forestry, Southwest University of Science and Technology, Mianyang, Sichuan 621010, China; Chengdu Institute of Research and Innovation, Southwest University of Science and Technology, Chengdu 610000, China. Electronic address:
Microbial remediation has prominent advantages in the prevention and control of uranium-contaminated soil. However, its efficiency in uranium immobilization remains suboptimal. Here, a biochar loaded mixed microorganisms was innovatively constructed, composed of Bacillus subtilis, Bacillus cereus, Pseudomonas putida, and Pseudomonas aeruginosa (3:2:2:3 ratio).
View Article and Find Full Text PDFWater Res
July 2025
School of Normal, East China University of Technology, Nanchang 330013, PR China.
Although uranium (U) bio-immobilization under aerobic conditions has been proven to be a viable bioremediation strategy, the roles of uranyl species and microbial metabolism related to specific hydrochemical components in U bio-immobilization are not well-understood. Groundwater samples were collected in a typical U-containing sandstone aquifer mined by acid in-situ leaching to investigate the specific hydrochemical components that potentially affected uranyl species and microbial metabolism and subsequently U bio-immobilization in the presence of Bacillus subtilis. Results showed that groundwater in the decommissioned acid in-situ leaching U mining area was characterized by low pH and high concentrations of U, SO, Ca, Mg, K, TOC, and F.
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