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生物炭和草酸能否缓解土壤微生物群落中多环芳烃的毒性胁迫?

Can biochar and oxalic acid alleviate the toxicity stress caused by polycyclic aromatic hydrocarbons in soil microbial communities?

机构信息

Key Laboratory of Soil Environment and Pollution Remediation, Institute of Soil Science, Chinese Academy of Sciences, Nanjing 210008, China; University of the Chinese Academy of Sciences, Beijing 100049, China.

Key Laboratory of Soil Environment and Pollution Remediation, Institute of Soil Science, Chinese Academy of Sciences, Nanjing 210008, China; University of the Chinese Academy of Sciences, Beijing 100049, China.

出版信息

Sci Total Environ. 2019 Dec 10;695:133879. doi: 10.1016/j.scitotenv.2019.133879. Epub 2019 Aug 12.

Abstract

It remains unclear whether biochar amendment can mediate changes in soil microbial communities caused by organic contaminants in the rhizosphere. In this study, phenanthrene-contaminated soil was amended with biochar and oxalic acid (OA) alone or in combination and incubated for 21 days. Phospholipid fatty acids (PLFAs) and high-throughput sequencing were used to evaluate shifts in bacterial and fungal community structure. Phenanthrene stress led to significant shifts in both soil bacterial and fungal community structure, in particularly, 82% of microbial phyla decreased in abundance. Biochar and/or OA improved the phenanthrene-polluted soil by positively mediating shifts in soil microbial communities stressed by phenanthrene. Specifically, biochar and/or OA led to the survival of certain microbial taxa that were inhibited by phenanthrene stress. In addition, many functional microbial individuals and genes participating in polycyclic aromatic hydrocarbon (PAH) degradation were positively stimulated by high phenanthrene stress and further stimulated by the simultaneous application of biochar and OA. Based on these findings, tandem biochar and rhizoremediation may be a feasible strategy for relieving PAH toxicity to soil microbial communities.

摘要

生物炭改良是否可以调节根际有机污染物引起的土壤微生物群落变化尚不清楚。在这项研究中,单独或联合添加生物炭和草酸(OA)来改良受菲污染的土壤,并培养 21 天。采用磷脂脂肪酸(PLFA)和高通量测序来评估细菌和真菌群落结构的变化。菲的胁迫导致土壤细菌和真菌群落结构发生显著变化,特别是 82%的微生物门丰度降低。生物炭和/或 OA 通过对受菲胁迫的土壤微生物群落的变化进行积极调节,改善了受菲污染的土壤。具体而言,生物炭和/或 OA 使某些受菲胁迫抑制的微生物类群得以存活。此外,许多参与多环芳烃(PAH)降解的功能微生物个体和基因受到高菲胁迫的正向刺激,并进一步受到生物炭和 OA 同时应用的刺激。基于这些发现,生物炭和根际修复的串联可能是缓解 PAH 对土壤微生物群落毒性的可行策略。

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