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Dynamics of soil amino sugar pools during decomposition processes of corn residues as affected by inorganic N addition

机译:无机氮添加对玉米残渣分解过程中土壤氨基糖库动态的影响

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摘要

Purpose Identifying the impact of inorganic-nitrogen (N) availability on soil amino sugar dynamics during corn (Zea mays L.) residue decomposition may advance our knowledge of microbial carbon (C) and N transformations and the factors controlling these processes in soils. Amino sugars are routinely used as microbial biomarkers to investigate C and N sequestration in microbial residues, and they are also involved in microbial-mediated soil organic matter (SOM) turnover. We conducted a 38-week incubation study using a Mollisol which was amended with corn residues and four levels of inorganic N (i.e., 0, 60.3, 167.2, and 701.9 mg N kg~(-1) soil). The objective of this study was to examine the effects of inorganic-N availability on fungal and bacterial formation and stabilization of heterogeneous amino sugars during the corn residue decomposition in soil.rnMaterials and methods The surface soil (0-20 cm) used for the experiment was taken from a site in Gongzhuling, Jilin Province of China (43°30'N, 124°48'E). The sampled soils were air-dried, mixed, and passed through a 2-mm sieve.rnThe incubation experiments were carried out at 25 ℃, and soil moisture was maintained at 20% gravimetric moisture content by regularly weighing the plastic containers and adding water to the plastic containers during the incubation if necessary. The incubation was destructively sampled at weeks 1, 2, 4, 8, 12, 18, 28, and 38 of the incubation. The whole samples were air-dried, ground (0.25 mm), and analyzed for amino sugar composition and concentration. Amino sugars (D-glucosamine, D-galactosamine, D-muramic acid, and D-mannosamine) were determined by capillary gas chromatography (GC) after their conversion to aldonitrile acetates (Zhang and Amelung 1996). Results and discussion Soil amino sugar contents and their contribution to SOM accumulation were significantly enhanced by the incorporation of corn residues, and amino sugar concentration maxima were observed during the 38-week-incubation course. Inorganic nitrogen significantly affected the accumulation of amino sugars during the decomposition of corn residues which had a high C/N ratio. It was found that more amino sugars were accumulated with higher inorganic N addition rates. However, when very high N application rates were evaluated, excess inorganic N in soil could not be taken up by microorganisms and some remained as inorganic N in the soil at the end of the incubation. Moreover, the dynamics of the individual amino sugars were different in response to the level of applied inorganic N. Muramic acid, a constituent of bacterial cell walls, was more sensitive to inorganic N supply and showed a faster turnover rate, while glucosamine, a constituent of fungal cell walls, was less sensitive to inorganic N supply. Glucosamine accumulated during the decay process of corn residues, and it was eventually stabilized in the soil.rnConclusions When corn residues were decomposing, individual amino sugar pools were affected by inorganic N addition. Bacterial cell-wall residues played an important role in soil N transformation in the early stages of corn residue decomposition, however, bacterial residues were rapidly remineralized. In the later stages of residue decomposition, amino sugars were assimilated into fungal cell walls which accumulated in soil and contributed to the long-term maintenance of SOM. Therefore, when plant residues with a high C/N ratio are incorporated into the soil, sufficient inorganic N is required for microbial growth. The addition of inorganic N to soils which have received plant residues with C/N ratio ≥ 30:1 is required to sustain microbial rapid growth; however, oversupply of inorganic N may increase the risk of inorganic N losses from agricultural fields.
机译:目的确定玉米(Zea mays L.)残留分解过程中无机氮(N)的可用性对土壤氨基糖动力学的影响,可能会提高我们对微生物碳(C)和N转化以及控制土壤中这些过程的因素的认识。氨基糖通常用作微生物生物标志物,以研究微生物残留物中的C和N螯合,并且它们还参与微生物介导的土壤有机质(SOM)转化。我们使用Mollisol进行了38周的温育研究,该Mollisol经过玉米残留物和4种无机N水平(即0、60.3、167.2和701.9 mg N kg〜(-1)土壤)的修正。这项研究的目的是研究土壤中玉米残留物分解过程中无机氮的有效利用对真菌和细菌形成以及异质氨基糖稳定化的影响。材料和方法用于实验的表层土壤(0-20厘米)取自中国吉林省公主岭市的一块遗址(北纬43°30',东经124°48')。将采样的土壤风干,混合并通过2毫米的筛子。在25℃下进行温育实验,通过定期称重塑料容器并向其中添加水,将土壤水分保持在20%的重量水分含量下。如果需要,在孵育过程中使用塑料容器。在孵育的第1、2、4、8、12、18、28和38周时以破坏性方式取样孵育。将整个样品风干,研磨(0.25mm),并分析氨基糖的组成和浓度。氨基糖(D-葡萄糖胺,D-半乳糖胺,D-山梨酸和D-甘露糖胺)在转化为乙酸乙二醛后,通过毛细管气相色谱(GC)测定(Zhang和Amelung 1996)。结果与讨论通过掺入玉米残渣,土壤氨基糖含量及其对SOM积累的贡献显着提高,在38周的培养过程中观察到氨基糖浓度最高。在高C / N比的玉米残渣分解过程中,无机氮显着影响氨基糖的积累。发现更多的氨基糖以更高的无机氮添加速率积累。然而,当评估氮的施用量非常高时,土壤中过量的无机氮无法被微生物吸收,并且在培养结束时,一些残留的无机氮仍作为土壤中的无机氮残留。此外,各个氨基糖的动力学响应于所施用的无机N的水平而有所不同。细菌细胞壁的组成部分-氨基甲酸对无机N的供应更为敏感,并且显示出更快的周转速度,而葡萄糖-氨基糖的组成更快真菌细胞壁对无机氮的供应较不敏感。葡萄糖胺在玉米残留物的腐烂过程中积累,并最终稳定在土壤中。rn结论当玉米残留物分解时,单个氨基酸糖库会受到无机氮的添加的影响。细菌细胞壁残留物在玉米残留物分解的早期阶段在土壤氮转化中起着重要作用,但是细菌残留物迅速被矿化。在残留物分解的后期,氨基糖被吸收到真菌细胞壁中,这些细胞壁在土壤中积累并有助于SOM的长期维持。因此,当将具有高C / N比的植物残渣掺入土壤中时,微生物生长需要足够的无机氮。为了保持微生物的快速生长,需要向已接收到C / N比≥30:1的植物残渣的土壤中添加无机氮。但是,无机氮的过量供应可能会增加农田中无机氮损失的风险。

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  • 来源
    《Journal of soil & sediments》 |2010年第4期|p.758-766|共9页
  • 作者单位

    Key Laboratory of Terrestrial Ecological Process, Institute of Applied Ecology, Chinese Academy of Sciences, Shenyang 110016, People's Republic of China Graduate University of Chinese Academy of Sciences, Beijing 100039, People's Republic of China;

    rnKey Laboratory of Terrestrial Ecological Process, Institute of Applied Ecology, Chinese Academy of Sciences, Shenyang 110016, People's Republic of China National Field Research Station of Shenyang Agroecosystems, Chinese Academy of Sciences, Shenyang 110016, People's Republic of China;

    rnKey Laboratory of Terrestrial Ecological Process, Institute of Applied Ecology, Chinese Academy of Sciences, Shenyang 110016, People's Republic of China;

    rnKey Laboratory of Terrestrial Ecological Process, Institute of Applied Ecology, Chinese Academy of Sciences, Shenyang 110016, People's Republic of China;

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  • 原文格式 PDF
  • 正文语种 eng
  • 中图分类
  • 关键词

    amino sugar; corn residues; inorganic nitrogen; soil organic matter;

    机译:氨基糖;玉米渣;无机氮土壤有机质;

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