Heuer H, Krsek M, Baker P, Smalla K, Wellington E M
Federal Biological Research Center for Agriculture and Forestry, Institute for Biochemistry and Plant Virology, Braunschweig, Germany.
Appl Environ Microbiol. 1997 Aug;63(8):3233-41. doi: 10.1128/aem.63.8.3233-3241.1997.
A group-specific primer, F243 (positions 226 to 243, Escherichia coli numbering), was developed by comparison of sequences of genes encoding 16S rRNA (16S rDNA) for the detection of actinomycetes in the environment with PCR and temperature or denaturing gradient gel electrophoresis (TGGE or DGGE, respectively). The specificity of the forward primer in combination with different reverse ones was tested with genomic DNA from a variety of bacterial strains. Most actinomycetes investigated could be separated by TGGE and DGGE, with both techniques giving similar results. Two strategies were employed to study natural microbial communities. First, we used the selective amplification of actinomycete sequences (E. coli positions 226 to 528) for direct analysis of the products in denaturing gradients. Second, a nested PCR providing actinomycete-specific fragments (E. coli positions 226 to 1401) was used which served as template for a PCR when conserved primers were used. The products (E. coli positions 968 to 1401) of this indirect approach were then separated by use of gradient gels. Both approaches allowed detection of actinomycete communities in soil. The second strategy allowed the estimation of the relative abundance of actinomycetes within the bacterial community. Mixtures of PCR-derived 16S rDNA fragments were used as model communities consisting of five actinomycetes and five other bacterial species. Actinomycete products were obtained over a 100-fold dilution range of the actinomycete DNA in the model community by specific PCR; detection of the diluted actinomycete DNA was not possible when conserved primers were used. The methods tested for detection were applied to monitor actinomycete community changes in potato rhizosphere and to investigate actinomycete diversity in different soils.
通过比较编码16S rRNA(16S rDNA)的基因序列,开发了一种属特异性引物F243(大肠杆菌编号中的第226至243位),用于通过PCR以及温度或变性梯度凝胶电泳(分别为TGGE或DGGE)检测环境中的放线菌。将正向引物与不同反向引物组合的特异性用来自多种细菌菌株的基因组DNA进行了测试。大多数研究的放线菌可以通过TGGE和DGGE分离,两种技术给出的结果相似。采用了两种策略来研究自然微生物群落。首先,我们使用放线菌序列(大肠杆菌第226至528位)的选择性扩增来直接分析变性梯度中的产物。其次,使用提供放线菌特异性片段(大肠杆菌第226至1401位)的巢式PCR,当使用保守引物时,该片段用作PCR的模板。然后使用梯度凝胶分离这种间接方法的产物(大肠杆菌第968至1401位)。两种方法都能够检测土壤中的放线菌群落。第二种策略可以估计放线菌在细菌群落中的相对丰度。PCR衍生的16S rDNA片段混合物用作由五种放线菌和五种其他细菌物种组成的模型群落。通过特异性PCR在模型群落中放线菌DNA的100倍稀释范围内获得放线菌产物;当使用保守引物时,无法检测稀释的放线菌DNA。所测试的检测方法用于监测马铃薯根际放线菌群落的变化,并研究不同土壤中放线菌的多样性。