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土壤特性限制了植物修复过程中微生物群落及其相关烃类降解基因的响应。

Soil Characteristics Constrain the Response of Microbial Communities and Associated Hydrocarbon Degradation Genes during Phytoremediation.

机构信息

Centre Armand Frappier Santé Biotechnologie, Institut National de la Recherche Scientifique, Université du Québec, Laval, Quebec, Canada.

Laurentian Forest Center, Natural Resources Canada, Québec City, Quebec, Canada.

出版信息

Appl Environ Microbiol. 2021 Jan 4;87(2). doi: 10.1128/AEM.02170-20.

DOI:10.1128/AEM.02170-20
PMID:33097512
原文链接:https://pmc.ncbi.nlm.nih.gov/articles/PMC7783334/
Abstract

Rhizodegradation is a promising cleanup technology where microorganisms degrade soil contaminants in the rhizosphere. A symbiotic relationship is expected to occur between plant roots and soil microorganisms in contaminated soils that enhances natural microbial degradation. However, little is known about how different initial microbiotas influence the rhizodegradation outcome. Recent studies have hinted that soil initial diversity has a determining effect on the outcome of contaminant degradation. To test this, we either planted (P) or not (NP) balsam poplars () in two soils of contrasting diversity (agricultural and forest) that were contaminated or not with 50 mg kg of phenanthrene (PHE). The DNA from the rhizosphere of the P and the bulk soil of the NP pots was extracted and the bacterial genes encoding the 16S rRNA, the PAH ring-hydroxylating dioxygenase alpha subunits (PAH-RHDα) of Gram-positive and Gram-negative bacteria, and the fungal ITS region were sequenced to characterize the microbial communities. The abundances of the PAH-RHDα genes were quantified by real-time quantitative PCR. Plant presence had a significant effect on PHE degradation only in the forest soil, whereas both NP and P agricultural soils degraded the same amount of PHE. Fungal communities were mainly affected by plant presence, whereas bacterial communities were principally affected by the soil type, and upon contamination the dominant PAH-degrading community was similarly constrained by soil type. Our results highlight the crucial importance of soil microbial and physicochemical characteristics in the outcome of rhizoremediation. Polycyclic aromatic hydrocarbons (PAH) are a group of organic contaminants that pose a risk to ecosystems' health. Phytoremediation is a promising biotechnology with the potential to restore PAH-contaminated soils. However, some limitations prevent it from becoming the remediation technology of reference, despite being environmentally friendlier than mainstream physicochemical alternatives. Recent reports suggest that the original soil microbial diversity is the key to harnessing the potential of phytoremediation. Therefore, this study focused on determining the effect of two different soil types in the fate of phenanthrene (a polycyclic aromatic hydrocarbon) under balsam poplar remediation. Poplar increased the degradation of phenanthrene in forest, but not in agricultural soil. The fungi were affected by poplars, whereas total bacteria and specific PAH-degrading bacteria were constrained by soil type, leading to different degradation patterns between soils. These results highlight the importance of performing preliminary microbiological studies of contaminated soils to determine whether plant presence could improve remediation rates or not.

摘要

根际降解是一种很有前途的清理技术,其中微生物在根际降解土壤污染物。在受污染的土壤中,植物根系和土壤微生物之间预计会形成共生关系,从而增强自然微生物降解。然而,人们对不同初始微生物群落如何影响根际降解结果知之甚少。最近的研究表明,土壤初始多样性对污染物降解的结果有决定性影响。为了验证这一点,我们在两种具有不同多样性的土壤(农业和森林)中种植(P)或不种植(NP)))(银柳),这两种土壤要么受到 50mg kg 菲的污染,要么没有受到污染。从 P 的根际和 NP 盆的大块土壤中提取 DNA,并对革兰氏阳性和革兰氏阴性细菌的 16S rRNA、多环芳烃环羟化双加氧酶α亚基(PAH-RHDα)和真菌 ITS 区的细菌基因进行测序,以表征微生物群落。通过实时定量 PCR 定量测定 PAH-RHDα 基因的丰度。植物的存在仅对森林土壤中的菲降解有显著影响,而农业土壤 NP 和 P 降解的菲量相同。真菌群落主要受植物存在的影响,而细菌群落主要受土壤类型的影响,并且在受到污染时,主要的多环芳烃降解群落同样受到土壤类型的限制。我们的结果强调了土壤微生物和理化特性在根际修复结果中的重要性。多环芳烃(PAH)是一组对生态系统健康构成风险的有机污染物。植物修复是一种很有前途的生物技术,具有修复多环芳烃污染土壤的潜力。然而,尽管它比主流物理化学替代方法更环保,但一些限制因素使其无法成为参考修复技术。最近的报告表明,原始土壤微生物多样性是利用植物修复潜力的关键。因此,本研究旨在确定在银柳修复下,两种不同土壤类型对菲(多环芳烃)命运的影响。杨树增加了森林中菲的降解,但在农业土壤中没有。真菌受杨树影响,而总细菌和特定的 PAH 降解细菌受土壤类型限制,导致土壤之间的降解模式不同。这些结果强调了在进行植物修复之前对污染土壤进行初步微生物研究的重要性,以确定植物的存在是否可以提高修复率。