Department of Environmental Sciences, University of California, Riverside, Riverside, CA 92521, USA.
Department of Environmental Sciences, University of California, Riverside, Riverside, CA 92521, USA.
Chemosphere. 2019 Sep;231:93-102. doi: 10.1016/j.chemosphere.2019.05.145. Epub 2019 May 18.
Because of their toxic properties, polycyclic aromatic hydrocarbons (PAHs) are designated as priority pollutants. The low solubility and strong sorption of PAHs in soil often limits bioremediation. To increase PAH bioavailability and enhance microbial degradation, surfactants are often added to contaminated soils. However, the effects of surfactants on the PAH degradation capacities of soil microbes are generally neglected. In this study, 16S rRNA gene high-throughput sequencing was used to evaluate changes in the soil microbial community after the application of rhamnolipid biosurfactant or Brij-35 surfactant and Mycobacterium vanbaalenii PYR-1 bioaugmentation over a 50-d mineralization study in two soils contaminated with pyrene at 10 mg kg. The introduction of pyrene in both soils resulted in an increase in Firmicutes and a decrease in microbial richness and Shannon diversity index. Amendment of rhamnolipid at 1,400 μg g to the native clay soil resulted in a decrease in Bacillus from 48% to 2%, which was accompanied with an increase in Mycoplana that accounted for 67% of the total genera relative abundance. Phylogenetic investigation of communities by reconstruction of unobserved states was used to predict the activity of functional genes involved in the PAH degradation KEGG pathway and determined that M. vanbaalenii PYR-1 bioaugmentation resulted in an increased number of functional genes utilized in PAH biodegradation. Results of this study provide a better understanding of the soil microbial dynamics in response to surfactant amendments in addition to bioaugmentation of a PAH-degrading microbe. This knowledge contributes to successful and efficient surfactant-enhanced bioremediation of PAH-contaminated soils.
由于其毒性,多环芳烃(PAHs)被指定为优先污染物。PAHs 在土壤中的低溶解度和强吸附性通常限制了生物修复。为了提高 PAH 的生物利用度并增强微生物降解,通常会向污染土壤中添加表面活性剂。然而,表面活性剂对土壤微生物 PAH 降解能力的影响通常被忽视。在这项研究中,采用 16S rRNA 基因高通量测序技术,在两种受芘污染的土壤中进行了 50 天的矿化研究,评估了添加鼠李糖脂生物表面活性剂或 Brij-35 表面活性剂以及接种分枝杆菌 PYR-1 生物强化后土壤微生物群落的变化,芘的添加量为 10mg/kg。两种土壤中引入芘后,厚壁菌门的丰度增加,微生物丰富度和 Shannon 多样性指数降低。在天然粘土地中添加 1400μg/g 的鼠李糖脂会使芽孢杆菌的丰度从 48%降低到 2%,同时伴随着微菌属的增加,占总属相对丰度的 67%。未观察到状态的群落重建的系统发育分析用于预测参与 PAH 降解 KEGG 途径的功能基因的活性,并确定分枝杆菌 PYR-1 生物强化导致用于 PAH 生物降解的功能基因数量增加。这项研究的结果提供了对土壤微生物动态的更好理解,这些动态响应于表面活性剂的添加以及 PAH 降解微生物的生物强化。这些知识有助于成功高效地进行受 PAH 污染土壤的表面活性剂增强生物修复。