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链霉菌产生的铁载体——重金属污染土壤中高铁氧肟酸盐的稳定性及变化

Siderophore production by streptomycetes-stability and alteration of ferrihydroxamates in heavy metal-contaminated soil.

作者信息

Schütze Eileen, Ahmed Engy, Voit Annekatrin, Klose Michael, Greyer Matthias, Svatoš Aleš, Merten Dirk, Roth Martin, Holmström Sara J M, Kothe Erika

机构信息

Microbial Communication, Institute of Microbiology, Faculty of Biology and Pharmacy, Friedrich Schiller University Jena, Neugasse 25, 07745, Jena, Germany.

Department of Geological Sciences, Stockholm University, Svante Arrhenius väg 8, 10691, Stockholm, Sweden.

出版信息

Environ Sci Pollut Res Int. 2015 Dec;22(24):19376-83. doi: 10.1007/s11356-014-3842-3. Epub 2014 Nov 22.

Abstract

Heavy metal-contaminated soil derived from a former uranium mining site in Ronneburg, Germany, was used for sterile mesocosms inoculated with the extremely metal-resistant Streptomyces mirabilis P16B-1 or the sensitive control strain Streptomyces lividans TK24. The production and fate of bacterial hydroxamate siderophores in soil was analyzed, and the presence of ferrioxamines E, B, D, and G was shown. While total ferrioxamine concentrations decreased in water-treated controls after 30 days of incubation, the sustained production by the bacteria was seen. For the individual molecules, alteration between neutral and cationic forms and linearization of hydroxamates was observed for the first time. Mesocosms inoculated with biomass of either strain showed changes of siderophore contents compared with the non-treated control indicating for auto-alteration and consumption, respectively, depending on the vital bacteria present. Heat stability and structural consistency of siderophores obtained from sterile culture filtrate were shown. In addition, low recovery (32 %) from soil was shown, indicating adsorption to soil particles or soil organic matter. Fate and behavior of hydroxamate siderophores in metal-contaminated soils may affect soil properties as well as conditions for its inhabiting (micro)organisms.

摘要

取自德国罗讷堡一个 former uranium mining site 的重金属污染土壤,被用于无菌微宇宙实验,其中接种了具有极强金属抗性的奇异链霉菌 P16B - 1 或敏感对照菌株变铅青链霉菌 TK24。分析了土壤中细菌异羟肟酸铁载体的产生和归宿,并检测到了铁铵霉素 E、B、D 和 G 的存在。在孵育 30 天后,水处理对照中的总铁铵霉素浓度下降,而细菌持续产生铁载体。对于单个分子,首次观察到异羟肟酸在中性和阳离子形式之间的转变以及异羟肟酸的线性化。接种了任一菌株生物质的微宇宙与未处理对照相比,显示出铁载体含量的变化,分别表明了自身变化和消耗,这取决于存在的活细菌。展示了从无菌培养滤液中获得的铁载体的热稳定性和结构一致性。此外,从土壤中的回收率较低(32%),表明其吸附到土壤颗粒或土壤有机质上。金属污染土壤中异羟肟酸铁载体的归宿和行为可能会影响土壤性质以及其栖息(微)生物的生存条件。

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