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Carbon isotopic fractionation during decomposition of plant materials of different quality

机译:不同质量植物材料分解过程中的碳同位素分馏

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Changes in isotopic ~(13)C composition of solid residues and CO_2 evolved during decomposition of C_3 and C_4 plant materials were monitored over 10 months to determine carbon isotopic fractionation at successive stages of biodegradation. We selected plant materials of different chemical quality, e.g., Zea mays (leaves, stems, coarse roots, and fine roots), Lolium perenne (leaves and roots), Pinus pinaster (needles), and Cocos nucifera (coconut shell) and also characterized these by solid-state ~(13)C NMR. Roots were more lignified than aerial parts of the same species. Lignin was always depleted in ~(13)C (up to 5.2‰) as compared with cellulose from the same sample. Proteins were enriched in ~(13)C in C_3 plants but depleted in maize. Cumulative CO_2 evolved fitted a double-exponential model with two C pools of different lability. During early stages of decomposition, the CO_2-C released was usually ~(13)C depleted as compared with the initial substrate but enriched at posterior stages. Consequently, with ongoing decomposition, the solid residue became ~(13)C depleted, which could only partly be explained by an accumulation of lignin-C. The extension of the initial ~(13)C depleted CO_2-C phase was significantly correlated with the labile substrate C content, acid-detergent soluble fraction, and total N, pointing to a direct influence of plant quality on C isotopic dynamics during early stages of biodegradation. This isotopic fractionation can also lead to an underestimation of the contribution of plane residues to CO_2-C when incubated in soils. We discuss possible implications of these mechanisms of ~(13)C fraction in ecosystems.
机译:在10个月内监测了C_3和C_4植物材料分解过程中产生的固体残渣和CO_2的同位素〜(13)C组成的变化,以确定生物降解连续阶段的碳同位素分馏。我们选择了具有不同化学质量的植物材料,例如玉米(玉米),叶(茎,粗根和细根),黑麦草(叶和根),松树(针)和椰子(椰子壳),并对其进行了表征这些通过固态〜(13)C NMR测定。根比同一物种的地上部分木质化程度更高。与来自相同样品的纤维素相比,木质素总是在〜(13)C中耗尽(高达5.2‰)。在C_3植物中,蛋白质在〜(13)C中富集,而在玉米中则被耗尽。累积的CO_2演化具有双指数模型,该模型具有两个具有不同稳定性的C库。在分解的早期阶段,释放的CO_2-C与初始底物相比通常约〜(13)C耗尽,但在后期富集。因此,随着分解的进行,固体残留物被耗尽了〜(13)C,这只能部分由木质素-C的积累来解释。初始〜(13)C耗尽的CO_2-C相的扩展与不稳定的底物C含量,酸清洗性可溶级分和总氮显着相关,这表明植物质量对早期C同位素动态的直接影响。生物降解。当在土壤中孵育时,这种同位素分馏也会导致平面残留物对CO_2-C的贡献被低估。我们讨论了〜(13)C分数在生态系统中这些机制的可能含义。

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