Department of Technical 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 Technical Biogeochemistry, Helmholtz Centre for Environmental Research - UFZ, Permoserstr. 15, 04318 Leipzig, Germany.
Sci Total Environ. 2024 Mar 25;918:170643. doi: 10.1016/j.scitotenv.2024.170643. Epub 2024 Feb 5.
Glyphosate and nitrogen (N) or (P) phosphorus fertilizers are often applied in combination to agricultural fields. The additional P or N supply to microorganisms might drive glyphosate degradation towards sarcosine/glycine or aminomethylphosphonic acid (AMPA), and consequently determine the speciation of non-extractable residues (NERs): harmless biogenic NERs (bioNERs) or potentially hazardous xenobiotic NERs (xenoNERs). We therefore investigated the effect of P or N-fertilizers on microbial degradation of glyphosate and bioNER formation in an agricultural soil. Four different treatments were incubated at 20 °C for 75 days as follows; I: no fertilizer (2-C,N-glyphosate only, control), II: P-fertilizer (superphosphate + 2-C,N-glyphosate, effect of P-supply), III: N-fertilizer (ammonium nitrate + 2-C,N-glyphosate, effect of N-supply) and IV: N-fertilizer (N-ammonium nitrate + 2-C-glyphosate, differentiation between microbial assimilations of N: N-fertilizer versus N-glyphosate). We quantified C or N in mineralization, extractable residues, NERs and in amino acids (AAs). At the end, mineralization (36-41 % of the C), extractable 2-C,N-glyphosate/2-C-glyphosate (0.42-0.49 %) & N-AMPA (1.2 %), and C/N-NERs (40-43 % of the C, 40-50 % of the N) were comparable among treatments. Contrastingly, the N-NERs from N-fertlizer amounted to only 6.6 % of the N. Notably, N-fertilizer promoted an incorporation of C/N from 2-C,N-glyphosate into AAs and thus the formation of C/N-bioNERs. The C/N-AAs were as follows: 16-21 % (N-fertilizer) > 11-13 % (control) > 7.2-7.3 % (P-fertilizer) of the initially added isotope. 2-C,N-glyphosate was degraded via the sarcosine/glycine and AMPA simultaneously in all treatments, regardless of the treatment type. The percentage share of bioNERs within the NERs in the N-fertilized soil was highest (C: 80-82 %, N: 100 %) compared to 53 % (C & N, control) and to only 30 % (C & N, P-fertilizer). We thus concluded simultaneous N & glyphosate addition to soils could be beneficial for the environment due to the enhanced bioNER formation, while P & glyphosate application disadvantageous since it promoted xenoNER formation.
草甘膦和氮(N)或(P)磷肥料通常同时施用于农业领域。微生物的额外 P 或 N 供应可能会促使草甘膦降解为肌氨酸/甘氨酸或氨甲基膦酸(AMPA),并因此决定不可提取残留物(NER)的形态:无害的生物源性 NER(bioNER)或潜在的有害异生物质源性 NER(xenoNER)。因此,我们研究了 P 或 N 肥料对农业土壤中草甘膦微生物降解和 bioNER 形成的影响。四种不同的处理在 20°C 下孵育 75 天,如下所示:I:无肥料(仅 2-C,N-草甘膦,对照),II:P 肥料(过磷酸钙+2-C,N-草甘膦,P 供应的影响),III:N 肥料(硝酸铵+2-C,N-草甘膦,N 供应的影响)和 IV:N 肥料(N-硝酸铵+2-C-草甘膦,区分微生物对 N 的同化:N 肥料与 N-草甘膦)。我们量化了矿化、可提取残留物、NER 和氨基酸(AA)中的 C 或 N。最后,矿化(C 的 36-41%)、可提取的 2-C,N-草甘膦/2-C-草甘膦(0.42-0.49%)和 N-AMPA(1.2%)以及 C/N-NER(C 的 40-43%,N 的 40-50%)在处理之间相当。相比之下,N 肥料中的 N-NER 仅占 N 的 6.6%。值得注意的是,N 肥料促进了从 2-C,N-草甘膦到 AA 的 C/N 掺入,从而形成了 C/N-bioNER。C/N-AA 如下:16-21%(N 肥料)>11-13%(对照)>7.2-7.3%(P 肥料)初始添加的同位素。2-C,N-草甘膦在所有处理中均通过肌氨酸/甘氨酸和 AMPA 同时降解,无论处理类型如何。与 53%(C 和 N,对照)相比,在 N 施肥土壤中 bioNER 在 NER 中的百分比份额最高(C:80-82%,N:100%),而仅为 30%(C 和 N,P 施肥)。因此,我们得出结论,由于增强的 bioNER 形成,同时向土壤中添加 N 和草甘膦可能对环境有益,而 P 和草甘膦的应用则不利,因为它促进了异生物质源性 NER 的形成。