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Physiological and Transcriptional Studies of Cr(VI) Reduction under Aerobic and Denitrifying Conditions by an Aquifer-Derived Pseudomonad

机译:含水层衍生的Pseudomonad在有氧和反硝化条件下还原Cr(VI)的生理和转录研究

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摘要

Cr(VI) is a widespread groundwater contaminant that is a potent toxin, mutagen, and carcinogen. In situ reductive immobilization is a favored approach for Cr(VI) bioremediation, and Cr(VI) reduction has been reported in a variety of aerobic, facultative, and anaerobic bacteria, including a number of pseudomonads. However, studies comparing Cr(VI) reduction under aerobic and denitrifying conditions in the same organism are not available. We have conducted studies with strain RCH2, a bacterium similar to Pseudomonas stutzeri that we isolated from a Cr-contaminated aquifer. Cell suspension studies with lactate demonstrated that Cr(VI) reduction could occur under either denitrifying or aerobic conditions (at comparable specific rates) and that reduction was at least 20-fold more rapid when the terminal electron acceptor (i.e., nitrate or O_2) was present. Our results suggest that Cr(VI) reduction by strain RCH2 under either aerobic or denitrifying conditions is primarily cometabolic in the sense that the physiological electron acceptor (oxygen or nitrate) appears to be required. Under both aerobic and denitrifying conditions, the gene(s) associated with chromate reduction are not inducible by Cr. Continuous culture (chemostat) studies showed strong correlations (r~2 values >0.93) between nitrate reduction rate and the transcript copy number of either nirS (cytochrome cd_1 nitrite reductase) or narG (nitrate reductase a subunit). As our studies indicate that anaerobic Cr(VI) reduction by this pseudomonad requires active denrtrification and that denrtrification and chromate reduction rates are highly correlated (r~2 > 0.99), monitoring expression of such denrtrification genes in biostimulated aquifers could provide valuable proxy information for in situ chromate reduction by similar bacteria even if the specific genes involved in chromate reduction have not been identified. We also report incomplete removal of reduced Cr from solution and on artifacts in the widely used diphenylcarbazide assay for Cr(VI), most notably, its complete inactivation in the presence of millimolar nitrite.
机译:六价铬是一种广泛的地下水污染物,是有效的毒素,诱变剂和致癌物。原位还原固定化是Cr(VI)生物修复的一种首选方法,并且在多种需氧,兼性和厌氧细菌(包括许多假单胞菌)中都已报道了Cr(VI)的还原。但是,尚无研究比较有氧和反硝化条件下同一生物中六价铬的还原量。我们已经对菌株RCH2进行了研究,RCH2是一种与斯氏假单胞菌相似的细菌,是从受Cr污染的含水层中分离出来的。用乳酸进行的细胞悬浮研究表明,Cr(VI)的还原可在反硝化或好氧条件下(以相当的特定速率)发生,并且当末端电子受体(即硝酸盐或O_2)被还原时,还原速度至少快20倍。当下。我们的结果表明,在有氧或反硝化条件下,菌株RCH2还原Cr(VI)的代谢主要是可代谢的,因为似乎需要生理性电子受体(氧气或硝酸盐)。在好氧和反硝化条件下,铬都不能诱导与铬酸盐还原相关的基因。连续培养(化学稳定剂)研究表明,硝酸盐还原率与nirS(细胞色素cd_1亚硝酸还原酶)或narG(硝酸还原酶亚基)的转录本拷贝数之间存在很强的相关性(r〜2值> 0.93)。正如我们的研究表明,这种假单胞菌对厌氧的Cr(VI)的还原需要主动的去甲作用,并且去甲化作用和铬酸盐的还原速率高度相关(r〜2> 0.99),监测这种去甲化基因在生物刺激含水层中的表达可以提供有价值的替代信息。即使尚未鉴定出与铬酸盐还原相关的特定基因,也可通过类似细菌进行原位铬酸盐还原。我们还报告了从溶液中去除还原的Cr的不完全现象,以及在广泛使用的Cr(VI)的二苯卡巴肼测定法中的伪迹上,最明显的是在存在毫摩尔亚硝酸盐的情况下其完全失活。

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  • 来源
    《Environmental Science & Technology》 |2010年第19期|p.7491-7497|共7页
  • 作者单位

    Earth Sciences Division, Lawrence Berkeley National Laboratory, Berkeley, California 94720;

    rnEarth Sciences Division, Lawrence Berkeley National Laboratory, Berkeley, California 94720;

    rnEarth Sciences Division, Lawrence Berkeley National Laboratory, Berkeley, California 94720;

    rnEarth Sciences Division, Lawrence Berkeley National Laboratory, Berkeley, California 94720;

    rnEarth Sciences Division, Lawrence Berkeley National Laboratory, Berkeley, California 94720;

    rnEarth Sciences Division, Lawrence Berkeley National Laboratory, Berkeley, California 94720;

    rnEarth Sciences Division, Lawrence Berkeley National Laboratory, Berkeley, California 94720;

  • 收录信息 美国《科学引文索引》(SCI);美国《工程索引》(EI);美国《生物学医学文摘》(MEDLINE);美国《化学文摘》(CA);
  • 原文格式 PDF
  • 正文语种 eng
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  • 入库时间 2022-08-17 14:04:02

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