Earth and Environmental Sciences, Lawrence Berkeley National Laboratory, Berkeley, CA, USA.
Earth and Environmental Sciences, Lawrence Berkeley National Laboratory, Berkeley, CA, USA.
Chemosphere. 2019 Nov;235:440-446. doi: 10.1016/j.chemosphere.2019.06.056. Epub 2019 Jun 14.
Hexavalent chromium Cr(VI) is a common inorganic contaminant in industrial areas and represents a serious threat to human health due its toxicity. Here we report experimental results from a field-scale investigation of Cr(VI) bio-immobilization at Hanford 100H reservation, a U.S Department of Energy facility (Washington State, USA). Microbial Cr(VI) reduction was stimulated via injection of aC-labeled sodium lactate solution into the high-permeability aquifer consisting of gravel and coarse sand sediments. Concentrations and carbon isotope ratios of metabolites, including dissolved inorganic carbon and total organic carbon, and compound-specific analysis of acetate and propionate, together with phospholipid fatty acids (biomass) have been analyzed to help provide an understanding of the predominant redox processes accompanying Cr(VI) reduction. Results of our study indicate that the injection of an electron donor caused a sharp decrease of Cr(VI) concentration from ∼32 to ∼10 nM. Cr(VI) reduction was associated with a decrease in the concentration of carboxylic acids, such as lactate (∼6 mM to undetectable), propionate (∼9 mM to undetectable), and acetate (∼6 mM to undetectable), as well as dissolved inorganic carbon (30-10 mM C). Carbon isotope data indicate carbon transfers from the original substrate to organic byproducts and mineralized carbon. Concentrations of metabolites and stable isotope data as well as carbon isotope mass balance calculations were used to monitor biologically mediated reduction of Cr(VI).
六价铬 (Cr(VI)) 是工业区域中常见的无机污染物,由于其毒性,对人类健康构成严重威胁。在这里,我们报告了在美国能源部设施(华盛顿州,美国)汉福德 100H 保留地进行的 Cr(VI) 生物固定现场规模调查的实验结果。通过将 13C 标记的乳酸钠溶液注入由砾石和粗砂沉积物组成的高渗透含水层,刺激微生物 Cr(VI) 还原。已分析了包括溶解无机碳和总有机碳在内的代谢物的浓度和碳同位素比,以及乙酸盐和丙酸盐的化合物特异性分析,以及磷脂脂肪酸(生物量),以帮助了解伴随 Cr(VI) 还原的主要氧化还原过程。我们的研究结果表明,电子供体的注入导致 Cr(VI) 浓度从约 32 至约 10 nM 急剧下降。Cr(VI) 还原与羧酸浓度的降低有关,例如乳酸盐(约 6 mM 至不可检测)、丙酸盐(约 9 mM 至不可检测)和乙酸盐(约 6 mM 至不可检测),以及溶解无机碳(30-10 mM C)。碳同位素数据表明,碳从原始底物转移到有机副产物和矿化碳。代谢物浓度和稳定同位素数据以及碳同位素质量平衡计算被用于监测 Cr(VI) 的生物介导还原。