Adam Iris K U, Duarte Márcia, Pathmanathan Jananan, Miltner Anja, Brüls Thomas, Kästner Matthias
Department of Environmental Biotechnology, Helmholtz-Centre for Environmental Research-UFZ, Permoserstr. 15, Leipzig, Germany.
Microbial Interactions and Processes Research Group, Helmholtz Centre for Infection Research-HZI, Braunschweig, Germany.
AMB Express. 2017 Dec;7(1):7. doi: 10.1186/s13568-016-0306-9. Epub 2017 Jan 3.
Polycyclic aromatic hydrocarbons are distributed ubiquitously in the environment and form metabolites toxic to most organisms. Organic amendment of PAH contaminated soil with compost and farmyard manure has proven to be efficient for PAH bioremediation mediated by native microorganisms, even though information on the identity of PAH degraders in organic-amended soil is still scarce. Here we provide molecular insight into the bacterial communities in soil amended with compost or farmyard manure for which the degradation mass balances of C-labeled pyrene have been recently published and assess the relevant bacterial genera capable of degrading pyrene as a model PAH. We performed statistical analyses of bacterial genera abundance data based on total DNA and RNA (for comparison) extracted from the soil samples. The results revealed complex pyrene degrading communities with low abundance of individual degraders instead of a limited number of abundant key players. The bacterial degrader communities of the soil-compost mixture and soil fertilized with farmyard manure differed considerably in composition albeit showing similar degradation kinetics. Additional analyses were carried out on enrichment cultures and enabled the reconstruction of several nearly complete genomes, thus allowing to link microcosm and enrichment experiments. However, pyrene mineralizing bacteria enriched from the compost or unfertilized soil-compost samples did not dominate pyrene degradation in the soils. Based on the present findings, evaluations of PAH degrading microorganisms in complex soil mixtures with high organic matter content should not target abundant key degrading species, since the specific degraders may be highly diverse, of low abundance, and masked by high bacterial background.
多环芳烃在环境中广泛分布,并形成对大多数生物有毒的代谢产物。用堆肥和农家肥对多环芳烃污染土壤进行有机改良,已被证明对由本地微生物介导的多环芳烃生物修复有效,尽管关于有机改良土壤中多环芳烃降解菌的身份信息仍然匮乏。在此,我们对用堆肥或农家肥改良的土壤中的细菌群落进行了分子层面的研究,最近已公布了这些土壤中碳标记芘的降解质量平衡,并评估了能够降解作为模型多环芳烃的芘的相关细菌属。我们基于从土壤样品中提取的总DNA和RNA(用于比较)对细菌属丰度数据进行了统计分析。结果显示,芘降解群落复杂,单个降解菌丰度低,而非仅有少数几个占主导的关键菌。土壤 - 堆肥混合物和用农家肥施肥的土壤中的细菌降解菌群落在组成上有很大差异,尽管它们显示出相似的降解动力学。对富集培养物进行了额外分析,并能够重建几个近乎完整的基因组,从而能够将微观世界和富集实验联系起来。然而,从堆肥或未施肥的土壤 - 堆肥样品中富集的芘矿化细菌在土壤中的芘降解过程中并不占主导地位。基于目前的研究结果,对高有机质含量的复杂土壤混合物中多环芳烃降解微生物的评估不应针对占主导的关键降解物种,因为特定的降解菌可能高度多样、丰度低且被高细菌背景所掩盖。