Characterization of a Pyrethroid-Degrading Pseudomonas fulva Strain P31 and Biochemical Degradation Pathway of D-Phenothrin

被引:65
|
作者
Yang, Jingjing [1 ]
Feng, Yanmei [1 ]
Zhan, Hui [1 ]
Liu, Jie [2 ,3 ]
Yang, Fang [1 ]
Zhang, Kaiyang [1 ]
Zhang, Lianhui [1 ]
Chen, Shaohua [1 ]
机构
[1] South China Agr Univ, Integrat Microbiol Res Ctr, Guangdong Prov Key Lab Microbial Signals & Dis Co, State Key Lab Conservat & Utilizat Subtrop Agrobi, Guangzhou, Guangdong, Peoples R China
[2] South China Agr Univ, Minist Educ, Lab Insect Toxicol, Guangzhou, Guangdong, Peoples R China
[3] South China Agr Univ, Minist Educ, Key Lab Pesticide & Chem Biol, Guangzhou, Guangdong, Peoples R China
基金
中国国家自然科学基金;
关键词
bioremediation; D-phenothrin; Pseudomonas fulva; metabolites; degradation pathway; HYDROLYZING CARBOXYLESTERASE GENE; BETA-CYPERMETHRIN; FENPROPATHRIN BIODEGRADATION; WASTE-WATER; BIOAUGMENTATION; DELTAMETHRIN; PURIFICATION; INSECTICIDES; KINETICS; CLONING;
D O I
10.3389/fmicb.2018.01003
中图分类号
Q93 [微生物学];
学科分类号
071005 ; 100705 ;
摘要
D-phenothrin is one of the most popular pyrethroid insecticides for its broad spectrum and high insecticidal activity. However, continuous use of D-phenothrin has resulted in serious environmental contamination and raised public concern about its impact on human health. Biodegradation of D-phenothrin has never been investigated and its metabolic behaviors remain unknown. Here, a novel bacterial strain P31 was isolated from active sludge, which completely degraded (100%) D-phenothrin at 50 mg.L-1 in 72 h. Based on the morphology, 16S rRNA gene and Biolog tests, the strain was identified as Pseudomonas fulva. Biodegradation conditions were optimized as 29.5 degrees C and pH 7.3 by utilizing response surface methodology. Strain P31 depicted high tolerance and strong D-phenothrin degradation ability through hydrolysis pathway. Strain P31 degraded D-phenothrin at inhibition constant (K-i) of 482.1673 mg.L-1 and maximum specific degradation constant (q(max)) of 0.0455 h(-1) whereas critical inhibitor concentration remained as 41.1189 mg.L-1. The 3-Phenoxybenzaldehyde and 1,2-benzenedicarboxylic butyl dacyl ester were identified as the major intermediate metabolites of D-phenothrin degradation pathway through high-performance liquid chromatography and gas chromatography-mass spectrometry. Bioaugmentation of D-phenothrin-contaminated soils with strain P31 dramatically enhanced its degradation, and over 75% of D-phenothrin was removed from soils within 10 days. Moreover, the strain illustrated a remarkable capacity to degrade other synthetic pyrethroids, including permethrin, cyhalothrin, beta-cypermethrin, deltamethrin, fenpropathrin, and bifenthrin, exhibiting great potential in bioremediation of pyrethroid-contaminated environment.
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页数:12
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