Temporal changes of microbial community structure and nitrogen cycling processes during the aerobic degradation of phenanthrene

微生物种群生物学 氮气循环 环境化学 蛋白质细菌 生物降解 化学 硝基螺 反硝化 微生物降解 氮气 降级(电信) 食品科学 硝化作用 生物 细菌 微生物 生物化学 有机化学 16S核糖体RNA 电信 基因 遗传学 计算机科学
作者
Meihui Yi,Lilan Zhang,Cunli Qin,Peili Lu,Hongcheng Bai,Xiaohu Han,Shupei Yuan
出处
期刊:Chemosphere [Elsevier]
卷期号:286: 131709-131709 被引量:31
标识
DOI:10.1016/j.chemosphere.2021.131709
摘要

Phenanthrene (PHE) is frequently detected in worldwide soils. But it is still not clear that how the microbial community succession happens and the nitrogen-cycling processes alter during PHE degradation. In this study, the temporal changes of soil microbial community composition and nitrogen-cycling processes during the biodegradation of PHE (12 μg g−1) were explored. The results showed that the biodegradation of PHE followed the second-order kinetics with a half-life of 7 days. QPCR results demonstrated that the bacteria numbers increased by 67.1%–194.7% with PHE degradation, whereas, no significant change was observed in fungi numbers. Thus, high-throughput sequencing based on 16 S rRNA was conducted and showed that the abundances of Methylotenera, Comamonadaceae, and Nocardioides involved in PHE degradation and denitrification were significantly increased, while those of nitrogen-metabolism-related genera such as Nitrososphaeraceae, Nitrospira, Gemmatimonadacea were decreased in PHE-treated soil. Co-occurrence network analysis suggested that more complex interrelations were constructed, and Proteobacteria instead of Acidobacteriota formed intimate associations with other microbes in responding to PHE exposure. Additionally, the abundances of nifH and narG were significantly up-regulated in PHE-treated soil, while that of amoA especially AOAamoA was down-regulated. Finally, correlation analysis found several potential microbes (Methylotenera, Comamonadaceae, and Agromyces) that could couple PHE degradation and nitrogen transformation. This study confirmed that PHE could alter microbial community structure, change the native bacterial network, and disturb nitrogen-cycling processes.

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