Institute of Soil and Water Resources and Environmental Science, College of Environmental and Resource Sciences, Zhejiang Provincial Key Laboratory of Agricultural Resources and Environment, Zhejiang University, Hangzhou, China; Department of Environmental Sciences, College of Forestry, Henan Agricultural University, Zhengzhou, China.
Institute of Soil and Water Resources and Environmental Science, College of Environmental and Resource Sciences, Zhejiang Provincial Key Laboratory of Agricultural Resources and Environment, Zhejiang University, Hangzhou, China.
Sci Total Environ. 2021 Aug 10;781:146655. doi: 10.1016/j.scitotenv.2021.146655. Epub 2021 Mar 20.
Biodegradation is a promising way to reduce phenanthrene (PHE) in environment. PHE biodegradation by bioaugmentation of axenic and mixed cultures of Massilia sp. WF1 (a highly efficient PHE-degrading bacteria) and Phanerochaete chrysosporium (P. chrysosporium, an extensively researched model fungus in organic pollutant bioremediation) was investigated in aqueous and autoclaved/un-autoclaved soil cultures. In the liquid cultures, the strain WF1 could use PHE (ca. 10 mg L) as the sole carbon source, and the presence of d-fructose (500 mg L) had no obvious effect on its PHE degradation; while the opposite was observed for P. chrysosporium. The bioaugmentation of strain WF1 and P. chrysosporium co-culture showed the highest PHE-degradation efficiency, especially in the aqueous and the autoclaved soil (PHE, ca. 50 mg kg) cultures, indicating a synergistic interaction of the co-culture during PHE dissipation. It was further observed that the indigenous microorganisms (mainly the Gram-positive bacteria) played a dominant role during PHE biodegradation and showed an antagonistic action against the strain WF1-P. chrysosporium co-culture, which weakened the synergistic action of the co-culture in the un-autoclaved soil. Besides, the abundances of PAH-RHDα GP and nidA genes were negatively correlated with residual PHE in the soil. Our findings provide the scientific support for bioremediation of PAHs in environment.
生物降解是一种很有前途的减少环境中菲(PHE)的方法。本研究通过投加 Massilia sp. WF1(一种高效的 PHE 降解细菌)和黄孢原毛平革菌(Phanerochaete chrysosporium,一种在有机污染物生物修复中广泛研究的模式真菌)的纯培养和混合培养,考察了在水相和灭菌/未灭菌土壤中的生物强化降解菲。在液体培养中,WF1 菌株可以利用 PHE(约 10 mg L)作为唯一的碳源,而 d-果糖(500 mg L)的存在对其 PHE 降解没有明显影响;而黄孢原毛平革菌则相反。WF1 菌株和黄孢原毛平革菌共培养的生物强化表现出最高的 PHE 降解效率,特别是在水相和灭菌土壤(PHE,约 50 mg kg)培养中,表明共培养物在 PHE 降解过程中存在协同作用。进一步观察到,土著微生物(主要是革兰氏阳性菌)在 PHE 生物降解过程中起主导作用,并对 WF1-黄孢原毛平革菌共培养物表现出拮抗作用,这削弱了共培养物在未灭菌土壤中的协同作用。此外,多环芳烃 RHDα GP 和 nidA 基因的丰度与土壤中残留的 PHE 呈负相关。本研究结果为环境中多环芳烃的生物修复提供了科学依据。