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放射形土壤杆菌J14a对莠去津的生物降解及其在污染土壤生物修复中的应用

Biodegradation of atrazine by Agrobacterium radiobacter J14a and use of this strain in bioremediation of contaminated soil.

作者信息

Struthers J K, Jayachandran K, Moorman T B

机构信息

Departments of Microbiology, Iowa State University, Ames, Iowa 50011, USA.

出版信息

Appl Environ Microbiol. 1998 Sep;64(9):3368-75. doi: 10.1128/AEM.64.9.3368-3375.1998.

Abstract

We examined the ability of a soil bacterium, Agrobacterium radiobacter J14a, to degrade the herbicide atrazine under a variety of cultural conditions, and we used this bacterium to increase the biodegradation of atrazine in soils from agricultural chemical distribution sites. J14a cells grown in nitrogen-free medium with citrate and sucrose as carbon sources mineralized 94% of 50 microgram of [14C-U-ring]atrazine ml-1 in 72 h with a concurrent increase in the population size from 7.9 x 10(5) to 5.0 x 10(7) cells ml-1. Under these conditions cells mineralized the [ethyl-14C]atrazine and incorporated approximately 30% of the 14C into the J14a biomass. Cells grown in medium without additional carbon and nitrogen sources degraded atrazine, but the cell numbers did not increase. Metabolites produced by J14a during atrazine degradation include hydroxyatrazine, deethylatrazine, and deethyl-hydroxyatrazine. The addition of 10(5) J14a cells g-1 into soil with a low indigenous population of atrazine degraders treated with 50 and 200 microgram of atrazine g-1 soil resulted in two to five times higher mineralization than in the noninoculated soil. Sucrose addition did not result in significantly faster mineralization rates or shorten degradation lag times. However, J14a introduction (10(5) cells g-1) into another soil with a larger indigenous atrazine-mineralizing population reduced the atrazine degradation lag times below those in noninoculated treatments but did not generally increase total atrazine mineralization.

摘要

我们研究了土壤细菌放射形土壤杆菌J14a在各种培养条件下对除草剂阿特拉津的降解能力,并利用该细菌提高农业化学品分销点土壤中阿特拉津的生物降解率。在以柠檬酸盐和蔗糖作为碳源的无氮培养基中生长的J14a细胞,在72小时内将50微克/毫升[14C-U-环]阿特拉津中的94%矿化,同时细胞数量从7.9×10⁵个/毫升增加到5.0×10⁷个/毫升。在这些条件下,细胞将[乙基-14C]阿特拉津矿化,并将约30%的14C掺入J14a生物量中。在没有额外碳源和氮源的培养基中生长的细胞能降解阿特拉津,但细胞数量没有增加。J14a在阿特拉津降解过程中产生的代谢产物包括羟基阿特拉津、脱乙基阿特拉津和脱乙基-羟基阿特拉津。向阿特拉津降解菌原生数量较低的土壤中添加10⁵个/克J14a细胞,并分别用50微克/克和200微克/克土壤的阿特拉津处理,其矿化率比未接种的土壤高两到五倍。添加蔗糖并没有显著提高矿化速率或缩短降解延迟时间。然而,将J14a(10⁵个/克细胞)引入另一种原生阿特拉津矿化菌数量较多的土壤中,可使阿特拉津降解延迟时间缩短至低于未接种处理的水平,但总体上并没有增加阿特拉津的总矿化量。

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引用本文的文献

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How toxic are toxic chemicals in soil?土壤中的有毒化学物质毒性如何?
Environ Sci Technol. 1995 Nov;29(11):2713-7. doi: 10.1021/es00011a003.
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Dechlorination of Atrazine by a Rhizobium sp. Isolate.根瘤菌属分离株对莠去津的脱氯作用。
Appl Environ Microbiol. 1997 Mar;63(3):862-6. doi: 10.1128/aem.63.3.862-866.1997.
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Metabolism of the herbicide atrazine by Rhodococcus strains.红球菌菌株对除草剂阿特拉津的代谢作用
Appl Environ Microbiol. 1993 Jun;59(6):1955-9. doi: 10.1128/aem.59.6.1955-1959.1993.

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