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表皮葡萄球菌L-02细菌培养物对铬酸盐和硝酸盐的厌氧共还原作用

Anaerobic co-reduction of chromate and nitrate by bacterial cultures of Staphylococcus epidermidis L-02.

作者信息

Vatsouria A, Vainshtein M, Kuschk P, Wiessner A, D Kosolapov, Kaestner M

机构信息

Institute of Biochemistry and Physiology of Microorganisms, Russian Academy of Sciences, pr. Nauki 5, 142290, Pushchino, Russia.

出版信息

J Ind Microbiol Biotechnol. 2005 Sep;32(9):409-14. doi: 10.1007/s10295-005-0020-0. Epub 2005 Nov 3.

Abstract

Industrial wastewater is often polluted by Cr(VI) compounds, presenting a serious environmental problem. This study addresses the removal of toxic, mutagenic Cr(VI) by means of microbial reduction to Cr(III), which can then be precipitated as oxides or hydroxides and extracted from the aquatic system. A strain of Staphylococcus epidermidis L-02 was isolated from a bacterial consortium used for the remediation of a chromate-contaminated constructed wetland system. This strain reduced Cr(VI) by using pyruvate as an electron donor under anaerobic conditions. The aims of the present study were to investigate the specific rate of Cr(VI) reduction by the strain L-02, the effects of chromate and nitrate (available as electron acceptors) on the strain, and the interference of chromate and nitrate reduction processes. The presence of Cr(VI) decreased the growth rate of the bacterium. Chromate and nitrate reduction did not occur under sterile conditions but was observed during tests with the strain L-02. The presence of nitrate increased both the specific Cr(VI) reduction rate and the cell number. Under denitrifying conditions, Cr(VI) reduction was not inhibited by nitrite, which was produced during nitrate reduction. The average specific rate of chromate reduction reached 4.4 micromol Cr 10(10 )cells(-1 )h(-1), but was only 2.0 micromol Cr 10(10 )cells(-1 )h(-1) at 20 degrees C. The maximum specific rate was as high as 8.8-9.8 micromol Cr 10(10 )cells(-1 )h(-1). The role of nitrate in chromate reduction is discussed.

摘要

工业废水常常受到六价铬化合物的污染,这是一个严重的环境问题。本研究旨在通过微生物将有毒、具有致突变性的六价铬还原为三价铬,然后使其以氧化物或氢氧化物的形式沉淀并从水系统中去除。表皮葡萄球菌L-02菌株是从用于修复铬酸盐污染人工湿地系统的细菌群落中分离得到的。该菌株在厌氧条件下以丙酮酸作为电子供体来还原六价铬。本研究的目的是探究L-02菌株还原六价铬的特定速率、铬酸盐和硝酸盐(作为电子受体)对该菌株的影响以及铬酸盐和硝酸盐还原过程之间的相互干扰。六价铬的存在降低了细菌的生长速率。在无菌条件下不会发生铬酸盐和硝酸盐的还原,但在用L-02菌株进行测试时可以观察到这种还原现象。硝酸盐的存在提高了六价铬的特定还原速率和细胞数量。在反硝化条件下,六价铬的还原不受硝酸盐还原过程中产生的亚硝酸盐的抑制。铬酸盐还原的平均特定速率达到4.4微摩尔铬·10¹⁰个细胞⁻¹·小时⁻¹,但在20℃时仅为2.0微摩尔铬·10¹⁰个细胞⁻¹·小时⁻¹。最大特定速率高达8.8 - 9.8微摩尔铬·10¹⁰个细胞⁻¹·小时⁻¹。文中讨论了硝酸盐在铬酸盐还原中的作用。

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