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Lignin degradation during a laboratory incubation followed by 13C isotope analysis.

机译:实验室孵育后木质素降解,然后进行13C同位素分析。

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Recent in situ 13C studies suggest that lignin is not stabilised in soil in its polymerised form. However, the fate of its transformation products remains unknown. The objective of the present research was to provide the first comprehensive picture of the fate of lignin-derived C across its transformations processes: (1) C remaining as undecomposed lignin molecules, (2) C in newly formed humic substances, i.e. no longer identifiable as lignin-polymer C, (3) C in microbial biomass, (4) C mineralised as CO2, and (5) dissolved organic C. To achieve this objective, we designed an incubation experiment with 13C-labelled lignin where both elementary and molecular techniques were applied. Lignin was isolated from 13C labelled maize plants (13C-MMEL) and incubated in an agricultural soil for 44 weeks. Carbon mineralisation and stable isotope composition of the released CO2 were monitored throughout the incubation. Microbial utilisation of 13C-MMEL was measured seven times during the experiment. The turnover rate of the lignin polymer was assessed by 13C analysis of CuO oxidation products of soil lignin molecules. After 44 incubation weeks, 6.0% of initial 13C-MMEL carbon was mineralised, 0.8% was contained in the microbial biomass, and 0.1% was contained in dissolved organic C form. The compound-specific 13C data suggest that the remaining 93% were overwhelmingly in the form of untransformed lignin polymer. However, limited transformation into other humic substances potentially occurred, but could not be quantified because the yield of the CuO oxidation method proved somewhat variable with incubation time. The initial bacterial growth yield efficiency for MMEL was 31% and rapidly decreased to plateau of 8%. A two-pool first-order kinetics model suggested that the vast majority (97%) of MMEL lignin had a turnover time of about 25 years, which is similar to field-estimated turnover times for soil-extractable lignin but much longer than estimated turnover times for fresh plant-residue lignin. We conclude that natural lignin structures isolated from plants are rather unreactive in soil, either due to the lack of easily available organic matter for co-metabolism or due to enhanced adsorption properties. The data also suggest that fairly undecomposed lignin structures are the main reservoir of lignin-derived C in soils.
机译:最近的原位13C研究表明,木质素不能以其聚合形式稳定在土壤中。但是,其转型产品的命运仍然未知。本研究的目的是提供木质素衍生的C在其转化过程中的命运的第一张综合图:(1)C保留为未分解的木质素分子,(2)C在新形成的腐殖质中,即不再可识别作为木质素聚合物C,(3)微生物生物质中的C,(4)矿化为CO2的C,以及(5)溶解的有机C。为实现这一目标,我们设计了一种13C标记的木质素的保温实验,其中元素和分子技术被应用。从13C标记的玉米植物(13C-MMEL)中分离出木质素,并在农业土壤中孵育44周。在整个孵育过程中,监测释放出的CO2的碳矿化作用和稳定的同位素组成。在实验过程中,对13C-MMEL的微生物利用率进行了7次测量。木质素聚合物的周转率通过土壤木质素分子的CuO氧化产物的13C分析来评估。温育44周后,最初的13C-MMEL碳矿化了6.0%,微生物生物量中包含0.8%,溶解的有机C形式中包含0.1%。化合物特有的13C数据表明,剩余的93%绝大多数以未转化的木质素聚合物的形式存在。但是,可能会发生有限转化为其他腐殖质的现象,但由于CuO氧化方法的产率随孵育时间而有所变化,因此无法量化。 MMEL的初始细菌生长产量效率为31%,并迅速下降至8%的平稳期。一个两池一阶动力学模型表明,绝大多数(97%)的MMEL木质素的转换时间约为25年,这与土壤提取的木质素的现场估计转换时间相似,但比估计的转换时间长得多提取新鲜植物残基木质素的时间。我们得出的结论是,从植物中分离出来的天然木质素结构在土壤中几乎没有反应性,这归因于缺乏易于获得的用于共代谢的有机物质或由于增强了吸附性能。数据还表明,相当未分解的木质素结构是木质素衍生的C在土壤中的主要储集层。

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