Department of Environmental Biotechnology, Helmholtz-Centre for Environmental Research - UFZ, Permoserstr. 15, 04318 Leipzig, Germany; Department of Isotope Biogeochemistry, Helmholtz Centre for Environmental Research - UFZ, Permoserstr. 15, 04318 Leipzig, Germany; Department of Environmental Sciences, Forman Christian College (A Chartered University), Ferozepur Road, 54600 Lahore, Pakistan.
Department of Environmental Biotechnology, Helmholtz-Centre for Environmental Research - UFZ, Permoserstr. 15, 04318 Leipzig, Germany.
J Hazard Mater. 2023 Apr 5;447:130847. doi: 10.1016/j.jhazmat.2023.130847. Epub 2023 Jan 20.
Glyphosate can be biodegraded via the aminomethylphosponic acid (AMPA) and the sarcosine/glycine pathway leading to the formation of three intermediate products AMPA, sarcosine or glycine. The fate of the three intermediate compounds of glyphosate biodegradation including nature of non-extractable residues (NERs; harmless biogenic [NERs] versus hazardous xenobiotic [NERs]) in soils has not been investigated yet. This information is crucial for an assessment of environmental risks related to the speciation of glyphosate-derived NERs which may stem from glyphosate intermediates. Therefore, we incubated C- and N-labeled glyphosate (2-C,N-glyphosate) and its degradation product AMPA (C,N-AMPA), sarcosine (C,N-sarcosine) or glycine (C,N-glycine) in an agricultural soil separately for a period of 75 days. C-glycine and C-sarcosine mineralized rapidly compared to 2-C-glyphosate and C-AMPA. The mineralization of C-AMPA was lowest among all four compounds due to its persistent nature. Only 0.5% of the initially added 2-C,N-glyphosate and still about 30% of the initially added C,N-AMPA was extracted from soil after 75 days. The NERs formed from C,N-AMPA were mostly NERs as compared to other three compounds for which significant amounts of NERs were determined. We noticed 2-C,N-glyphosate was biodegraded via two biodegradation pathways simultaneously; however, the sarcosine/glycine pathway with the formation of harmless NERs presumably dominated.
草甘膦可通过氨甲基膦酸(AMPA)和肌氨酸/甘氨酸途径生物降解,导致形成三种中间产物 AMPA、肌氨酸或甘氨酸。草甘膦生物降解的三种中间化合物(包括无害生物源非提取残留[NERs]与有害外源 NERs)在土壤中的命运尚未得到研究。这些信息对于评估与草甘膦衍生 NERs 形态相关的环境风险至关重要,这些 NERs 可能源自草甘膦中间体。因此,我们分别在农业土壤中培养了 C 和 N 标记的草甘膦(2-C,N-草甘膦)及其降解产物 AMPA(C,N-AMPA)、肌氨酸(C,N-肌氨酸)或甘氨酸(C,N-甘氨酸),培养期为 75 天。与 2-C-草甘膦和 C-AMPA 相比,C-甘氨酸和 C-肌氨酸迅速矿化。由于其持久性,四种化合物中 C-AMPA 的矿化最低。75 天后,最初添加的 2-C,N-草甘膦中只有 0.5%,最初添加的 C,N-AMPA 中仍有约 30%从土壤中提取出来。与其他三种化合物相比,C,N-AMPA 形成的 NERs 大多是 NERs,因为这些化合物中确定了大量的 NERs。我们注意到 2-C,N-草甘膦通过两种生物降解途径同时进行生物降解;然而,形成无害 NERs 的肌氨酸/甘氨酸途径可能占据主导地位。