Institute of Military-Civilian Integration Technology, Northwest University of Political Science and Law, Xi'an, Shaanxi, 710122, China.
Institute of Military-Civilian Integration Technology, Northwest University of Political Science and Law, Xi'an, Shaanxi, 710122, China.
J Environ Radioact. 2024 Feb;272:107356. doi: 10.1016/j.jenvrad.2023.107356. Epub 2023 Dec 18.
The experimental and thermodynamic bioreduction of U(VI) and Pu(IV) was studied in order to more accurately predict their transport velocities in groundwater and assess the contamination risks to the associated environments. The results obtained in this study emphasize the impact of carbonate-calcium and humic acids at 7.1 and anoxic solutions on the rate and extent of U(VI) and Pu(IV) bioreduction by Shewanella putrefaciens. We found that the bioreduction rate of U(VI) became slow in the presence of NaHCO/CaCl. The more negative standard redox potentials of the ternary complexes of U(VI)-Ca-CO accounted for the decreased rate of bioreduction, e.g., [Formula: see text] = -0.6797 V ≪ [Formula: see text] = 0.3862 V. The bioreduction of Pu(IV) seemed feasible, while humic acids accepted the adequate extracellular electrons secreted by S. putrefaciens, and the redox potential of E(HA/HA) was lower than E(PuO(am)/Pu), e.g., E(HA/HA) ≦ E(PuO(am)/Pu) if humic acids accepted ≧ 7.952 × 10 mol of electrons. The standard redox potentials, E(PuO(am)/Pu) = 0.9295 V ≫ [Formula: see text] = -0.6797 V, cannot explain the reduction extent of Pu(IV) (8.9%), which is notably smaller than that of U(VI) (74.9%). In fact, the redox potential of Pu(IV) was distinctly negative under the experimental conditions of trace-level Pu(IV) (∼2.8 × 10 mol/L Pu(IV) if Pu(IV) was completely dissolved), e.g., E(PuO(am)/Pu) = -0.1590 V (α(Pu) = 10 mol/L, pH = 7.1). Therefore, the chemical factor of Pu activity, leading to a rapid drop in E(PuO(am)/Pu) at trace-level Pu(IV), was responsible for the relatively small reduction extent of Pu(IV).
为了更准确地预测 U(VI) 和 Pu(IV) 在地下水中的迁移速度,并评估其对相关环境的污染风险,研究了它们的实验和热力学生物还原。本研究结果强调了在 7.1 和缺氧溶液中,碳酸盐-钙和腐殖酸对 Shewanella putrefaciens 生物还原 U(VI) 和 Pu(IV) 的速率和程度的影响。我们发现,在存在 NaHCO/CaCl 的情况下,U(VI)的生物还原速率变慢。三元配合物 U(VI)-Ca-CO 的标准氧化还原电位更负,这解释了生物还原速率的降低,例如 [Formula: see text] = -0.6797 V ≪ [Formula: see text] = 0.3862 V。Pu(IV)的生物还原似乎是可行的,而腐殖酸接受了由 S. putrefaciens 分泌的足够的细胞外电子,并且 E(HA/HA)的氧化还原电位低于 E(PuO(am)/Pu),例如,如果腐殖酸接受的电子数量大于等于 7.952×10 mol,则 E(HA/HA)≦E(PuO(am)/Pu)。标准氧化还原电位,E(PuO(am)/Pu) = 0.9295 V ≫ [Formula: see text] = -0.6797 V,不能解释 Pu(IV)的还原程度(8.9%),明显小于 U(VI)的还原程度(74.9%)。事实上,在痕量 Pu(IV)(如果 Pu(IV)完全溶解,则约为 2.8×10 mol/L Pu(IV))的实验条件下,Pu(IV)的氧化还原电位明显为负,例如 E(PuO(am)/Pu) = -0.1590 V(α(Pu) = 10 mol/L,pH = 7.1)。因此,导致痕量 Pu(IV)时 E(PuO(am)/Pu)快速下降的 Pu 活性的化学因素是 Pu(IV)还原程度相对较小的原因。