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分离降解硝基苯的假单胞菌 NB001 及其在受污染水体生物修复中的应用。

Isolation of nitrobenzene degrading strain Pseudomonas NB001 and application in the bioremediation of polluted water body.

机构信息

College of Resources and Environment, Jilin Agricultural University, Changchun, PR China.

出版信息

J Environ Sci Health A Tox Hazard Subst Environ Eng. 2012;47(1):70-6. doi: 10.1080/10934529.2012.629583.

Abstract

A bacterium using nitrobenzene (NB) as a sole source of carbon, nitrogen and energy was isolated from NB-contaminated water body by the enrichment technology. It was identified as Pseudomonas NB001 by the phylogenetic analysis based on 16S rDNA sequence and the biochemical and physiological characteristics. Degradation of NB by strain NB001 was concomitant with the release of nitrite. Activities of catechol2,3-dioxygenase in strain NB001 cells grown in the culture fluid were higher than that in cells under any other conditions (P < 0.05). Under the pure culture conditions, 98.4% of NB at initial concentration of 50 mg L(-1) was removed in 136 hours. Glucose at starting concentration of 100 mg L(-1) delayed the onset of the exponential phase of NB degradation and weakened the degradation ability of per cell in the pure culture systems. In the river water, 89.5% of NB was degraded in 8 days. Suspended matter obviously increased the degradation rate of NB in the early stages, but decreased in the final stages. Cd(2+) and Hg(2+) significantly weakened the ability of the strain to degrade NB at initial concentrations of 10.0 mg L(-1) and 5.0 mg L(-1), respectively. The results would offer useful information for the application of strain NB001 in the bioremediation or the control of NB-contaminated environment.

摘要

从受硝苯(NB)污染的水体中,采用富集技术分离到一株以 NB 为唯一碳源、氮源和能源的细菌。根据 16S rDNA 序列和生化生理特性的系统发育分析,将其鉴定为 Pseudomonas NB001。NB001 菌株降解 NB 的同时伴随着亚硝酸盐的释放。在培养液中生长的 NB001 细胞中的儿茶酚 2,3-双加氧酶活性高于任何其他条件下的细胞(P<0.05)。在纯培养条件下,起始浓度为 50mg/L 的 NB 在 136 小时内去除了 98.4%。起始浓度为 100mg/L 的葡萄糖延迟了 NB 降解指数期的开始,并削弱了纯培养系统中每细胞的降解能力。在河水中,8 天内去除了 89.5%的 NB。悬浮物在早期明显提高了 NB 的降解速率,但在后期则降低了。Cd(2+)和 Hg(2+)的初始浓度分别为 10.0mg/L 和 5.0mg/L 时,显著削弱了该菌株降解 NB 的能力。这些结果为菌株 NB001 在 NB 污染环境的生物修复或控制中的应用提供了有用的信息。

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