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Vertical distribution of the methanotrophic community after drainage of rice field soil

机译:稻田土壤排水后甲烷营养群落的垂直分布

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Anoxic soils, such as flooded rice fields, are major sources of the greenhouse gas CH4 while oxic upland soils are major sinks of atmospheric CH4. Nevertheless, CHI is also consumed in rice fields where up to 90% of the produced CH4 is oxidized in a narrow oxic zone around the rice roars and in the soil surface layer before it escapes into the atmosphere. After 1 day drainage of rice field soil, CH4 oxidation was detected in the top 2-mm soil layers, but after 8 days drainage the zone of CH4 oxidation extended to 8 mm depth. Simultaneously, the potential For CH4 production decreased, but some production was still detectable after 8 days drainage throughout the soil profile. The vertical distribution of the methanotrophic community was also monitored after and 8 days drainage using denaturing gradient gel electrophoresis after PCR amplification with primer sets targeting two regions on the 16S rRNA gene that are relatively specific for methylotrophic alpha- and gamma -Proteobacteria, and targeting two functional genes encoding subunits of key enzymes in all methanotrophs, i.e. the genes for the particulate methane monooxygenase (pmoA) and the methanol dehydrogenase (mxaF). Drainage stimulated the methanotrophic community. Eight days after drainage, new methanotrophic populations appeared and a distinct methanotrophic community developed. The population structure of type I and II methanotrophs was differently affected by drainage. Type II methanotrophs (alpha -Prorteobacteria) were present throughout the soil core directly after drainage (1 day), and the community composition remained largely unchanged with di Dth. Only two new type II populations appeared after 8 days of drainage. Drainage had a more pronounced impact on the type I methanotrophic community (gamma -Proteobacteria). Type I populations were not or only weakly detected 1 day after drainage. However, after 8 days of drainage, a large diversity of type I methanotrophs were detected, altough they were not evenly distributed throughout the soil core but dominated at different depths. A distinct type I community structure had developed within each soil section between 0 and 20 mm soil depth, indicating the widening of suitable habitats For methanotrophs in the rice field soil within 1 week of drainage, (C) 2001 Federation of European Microbiological Societies. Published by Elsevier Science B.V. All rights reserved. [References: 42]
机译:缺水的土壤,例如淹没的稻田,是温室气体CH4的主要来源,而有氧的旱地土壤则是大气CH4的主要汇。尽管如此,CHI还被稻田消耗,在稻田中,高达90%的CH4在稻咆哮周围和土壤表层的狭窄氧化区中被氧化,然后逸出到大气中。稻田土壤排水1天后,在顶部2毫米土壤层中检测到CH4氧化,但排水8天后,CH4氧化区域扩展至8毫米深度。同时,CH4产生的潜力降低了,但在整个土壤剖面中排水8天后仍可检测到一些产生。在PCR扩增后变性变性梯度凝胶电泳和引物组靶向16S rRNA基因上相对于甲基营养型α-和γ-变形杆菌具有相对特异性的两个区域,并靶向两个在所有甲烷营养生物中编码关键酶亚基的功能基因,即颗粒甲烷单加氧酶(pmoA)和甲醇脱氢酶(mxaF)的基因。排水刺激了甲烷营养群落。排水八天后,出现了新的甲烷营养种群,并形成了一个独特的甲烷营养群落。 I和II型甲烷营养菌的种群结构受排水的影响不同。排水后(1天)直接在整个土壤核心中存在II型甲烷营养菌(α-原细菌),群落组成随Dth的变化基本保持不变。引流8天后仅出现了两个新的II型种群。排水对I型甲烷营养群落(γ-变形杆菌)有更明显的影响。引流后1天未或仅微弱地检测到I型种群。然而,排水8天后,发现了I型甲烷营养菌的多样性,尽管它们并非均匀分布在整个土壤核心中,但在不同深度占优势。在土壤深度介于0到20毫米之间的每个土壤区域中都形成了独特的I型群落结构,表明排水后1周内稻田土壤中的甲烷营养菌的适宜生境拓宽了(C)2001年欧洲微生物学会联合会。由Elsevier Science B.V.保留所有权利。 [参考:42]

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