Ouyang Wei-Ying, Kümmel Steffen, Adrian Lorenz, Zhu Yong-Guan, Richnow Hans H
Helmholtz Centre for Environmental Research - UFZ, Isotope Biogeochemistry, Leipzig, Germany; Chair of Geobiotechnology, Technische Universität Berlin, Berlin, Germany.
Helmholtz Centre for Environmental Research - UFZ, Isotope Biogeochemistry, Leipzig, Germany.
Chemosphere. 2023 Jan;311(Pt 2):136923. doi: 10.1016/j.chemosphere.2022.136923. Epub 2022 Oct 27.
The fate of antibiotics in aquatic environments is of high concern and approaches are needed to assess the transformation of antibiotics in wastewater treatment plants. Here we used the model organism Desulfovibrio vulgaris Hildenborough to analyze compound specific isotope fractionation associated with anaerobic transformation of the antibiotic sulfamethoxazole (SMX). The results show that the rearrangement of the isoxazole ring in SMX is leading to significant carbon and hydrogen isotopic fractionation (ε = -5.8 ± 0.7‰, ε = -34 ± 9‰) during anaerobic transformation. The observed carbon isotopic fractionation is significantly higher than the values reported for aerobic degradation (ε = -0.6 ± 0.1‰) or abiotic reactions (ε = -0.8 to -4.8‰ for photolysis, ε = -0.8 to -2.2‰ for advanced oxidation). This indicates that carbon isotope fractionation can be used as a parameter to differentiate reaction mechanisms of SMX transformation. The corresponding apparent kinetic isotope effect (AKIE) for anaerobic transformation of SMX was 1.029 ± 0.003, suggesting that the mechanism for anaerobic transformation is distinct from the mechanism reported for microbial aerobic degradation (AKIE = 1.006 ± 0.001). In addition, dual-element (C-H) isotope analysis of SMX was performed in the present study, which was achieved by utilizing gas chromatography (GC) as the separation method instead of routine liquid chromatography. This dual-element isotope analysis resulted in a Λ value of 4.5 ± 2.2. Overall, compound specific isotope analysis can be a feasible tool to monitor the mitigation of SMX in wastewater treatment plants.
抗生素在水生环境中的命运备受关注,需要采用相关方法来评估抗生素在污水处理厂中的转化情况。在此,我们使用模式生物希氏脱硫弧菌来分析与抗生素磺胺甲恶唑(SMX)厌氧转化相关的化合物特异性同位素分馏。结果表明,SMX中异恶唑环的重排在厌氧转化过程中导致了显著的碳和氢同位素分馏(ε = -5.8 ± 0.7‰,ε = -34 ± 9‰)。观察到的碳同位素分馏显著高于有氧降解(ε = -0.6 ± 0.1‰)或非生物反应(光解时ε = -0.8至-4.8‰,ε = -0.8至-2.2‰)所报道的值。这表明碳同位素分馏可作为区分SMX转化反应机制的一个参数。SMX厌氧转化的相应表观动力学同位素效应(AKIE)为1.029 ± 0.003,表明厌氧转化机制与微生物有氧降解所报道的机制不同(AKIE = 1.006 ± 0.001)。此外,本研究中对SMX进行了双元素(C-H)同位素分析,该分析通过使用气相色谱(GC)作为分离方法而非常规液相色谱来实现。这种双元素同位素分析得出的Λ值为4.5 ± 2.