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Physical disturbance to ecological niches created by soil structure alters community composition of methanotrophs.土壤结构造成的生态位物理干扰改变了产甲烷菌群落的组成。
Environ Microbiol Rep. 2011 Oct;3(5):613-21. doi: 10.1111/j.1758-2229.2011.00270.x. Epub 2011 Aug 22.
2
The functions of biological diversity in an age of extinction.生物多样性在灭绝时代的功能。
Science. 2012 Jun 15;336(6087):1401-6. doi: 10.1126/science.1215855.
3
Effects of disturbance intensity and frequency on bacterial community composition and function.干扰强度和频率对细菌群落组成和功能的影响。
PLoS One. 2012;7(5):e36959. doi: 10.1371/journal.pone.0036959. Epub 2012 May 14.
4
Microbial diversity affects self-organization of the soil-microbe system with consequences for function.微生物多样性影响土壤-微生物系统的自组织,从而影响其功能。
J R Soc Interface. 2012 Jun 7;9(71):1302-10. doi: 10.1098/rsif.2011.0679. Epub 2011 Dec 7.
5
A survey of the cellular responses in Pseudomonas putida KT2440 growing in sterilized soil by microarray analysis.利用基因芯片分析研究在灭菌土壤中生长的恶臭假单胞菌 KT2440 的细胞反应。
FEMS Microbiol Ecol. 2011 Nov;78(2):220-32. doi: 10.1111/j.1574-6941.2011.01146.x. Epub 2011 Jul 4.
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Navigating the multiple meanings of β diversity: a roadmap for the practicing ecologist.β 多样性的多重含义:实践生态学家的路线图。
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7
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Linking bacterial identities and ecosystem processes: can 'omic' analyses be more than the sum of their parts?将细菌身份与生态系统过程联系起来:“组学”分析能否不仅仅是其各部分的总和?
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A primer on metagenomics.元基因组学简介。
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Exploring improved endoglucanase expression in Saccharomyces cerevisiae strains.探索提高酿酒酵母菌株内切葡聚糖酶表达。
Appl Microbiol Biotechnol. 2010 May;86(5):1503-11. doi: 10.1007/s00253-009-2403-z. Epub 2009 Dec 30.

将微生物群落结构与土壤团聚体中的β-葡萄糖苷功能联系起来。

Linking microbial community structure to β-glucosidic function in soil aggregates.

机构信息

Microbiology, Pacific Northwest National Laboratory, Richland, WA, USA.

出版信息

ISME J. 2013 Oct;7(10):2044-53. doi: 10.1038/ismej.2013.87. Epub 2013 May 30.

DOI:10.1038/ismej.2013.87
PMID:23719152
原文链接:https://pmc.ncbi.nlm.nih.gov/articles/PMC3965315/
Abstract

To link microbial community 16S structure to a measured function in a natural soil, we have scaled both DNA and β-glucosidase assays down to a volume of soil that may approach a unique microbial community. β-Glucosidase activity was assayed in 450 individual aggregates, which were then sorted into classes of high or low activities, from which groups of 10 or 11 aggregates were identified and grouped for DNA extraction and pyrosequencing. Tandem assays of ATP were conducted for each aggregate in order to normalize these small groups of aggregates for biomass size. In spite of there being no significant differences in the richness or diversity of the microbial communities associated with high β-glucosidase activities compared with the communities associated with low β-glucosidase communities, several analyses of variance clearly show that the communities of these two groups differ. The separation of these groups is partially driven by the differential abundances of members of the Chitinophagaceae family. It may be observed that functional differences in otherwise similar soil aggregates can be largely attributed to differences in resource availability, rather than to the presence or absence of particular taxonomic groups.

摘要

为了将微生物群落 16S 结构与自然土壤中的实测功能联系起来,我们将 DNA 和β-葡萄糖苷酶测定法的规模缩小到可能接近单个微生物群落的土壤体积。β-葡萄糖苷酶活性在 450 个单个聚集体中进行测定,然后将其分为高活性或低活性两类,从中选择 10 或 11 个聚集体进行分组,用于 DNA 提取和焦磷酸测序。对每个聚集体进行 ATP 串联测定,以根据生物量大小对这些小聚集体组进行标准化。尽管与低β-葡萄糖苷酶活性相关的微生物群落的丰富度或多样性与高β-葡萄糖苷酶活性相关的微生物群落没有显著差异,但几个方差分析清楚地表明这两组的群落存在差异。这两组的分离部分是由几丁质分解菌科成员的丰度差异驱动的。可以观察到,在其他方面相似的土壤聚集体中的功能差异主要归因于资源可用性的差异,而不是特定分类群的存在或不存在。