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硫酸亚铁、接种历史和阴离子形态对嗜酸氧化亚铁硫杆菌 BC13 菌株铅、锌和铜毒性的影响。

Effects of ferrous sulfate, inoculum history, and anionic form on lead, zinc, and copper toxicity to Acidithiobacillus caldus strain BC13.

机构信息

Department of Chemical and Biological Engineering, Montana State University, Bozeman, Montana, USA.

出版信息

Environ Toxicol Chem. 2010 Dec;29(12):2669-75. doi: 10.1002/etc.338. Epub 2010 Oct 7.

Abstract

The current study reports the single and combined toxicities of Pb, Zn, and Cu to Acidithiobacillus caldus strain BC13. The observed half-maximal inhibitory concentrations (IC50), ± 95% confidence intervals, for Pb, Zn, and Cu were 0.9 ± 0.1 mM, 39 ± 0.5 mM, and 120 ± 8 mM, respectively. The observed minimum inhibitory concentrations (MIC) for Pb, Zn, and Cu were 7.5 mM, 75 mM, and 250 mM, respectively. When metals were presented in binary mixtures, the toxicities were less than additive. For example, when 50% of the Pb MIC and 50% of the Cu MIC were presented together, the specific growth rate was inhibited by only 59 ± 3%, rather than 100%. In addition, the presence of ferrous iron in the growth media decreased Pb and Zn toxicity to A. caldus strain BC13. The importance of inoculum history was evaluated by pre-adapting cultures through subsequent transfers in the presence of Pb, Zn, and Cu at their respective IC50s. After pre-adaptation, cultures had specific growth rates 39 ± 11, 32 ± 7, and 28 ± 12% higher in the presence of Pb, Zn, and Cu IC50s, respectively, compared with cultures that had not been pre-adapted. In addition, when cells exposed to the MICs of Pb, Zn, and Cu were harvested, washed, and re-inoculated into fresh, metal-free medium, they grew, showing that the cells remained viable with little residual toxicity. Finally, metal chlorides showed more toxicity than metal sulfates, and studies using sodium chloride or a mixture of metal sulfates and sodium chloride suggested that this was attributable to an additive combination of the metal and chloride toxicities.

摘要

本研究报告了 Pb、Zn 和 Cu 对嗜酸氧化亚铁硫杆菌 BC13 菌株的单一和联合毒性。观察到的 Pb、Zn 和 Cu 的半最大抑制浓度 (IC50) ± 95%置信区间分别为 0.9 ± 0.1 mM、39 ± 0.5 mM 和 120 ± 8 mM。观察到的 Pb、Zn 和 Cu 的最小抑菌浓度 (MIC) 分别为 7.5 mM、75 mM 和 250 mM。当金属以二元混合物形式存在时,毒性小于加性。例如,当 Pb 的 MIC 的 50%和 Cu 的 MIC 的 50%同时存在时,比生长速率仅抑制了 59 ± 3%,而不是 100%。此外,生长培养基中存在二价铁会降低 Pb 和 Zn 对 A. caldus 菌株 BC13 的毒性。通过在各自的 IC50 下用 Pb、Zn 和 Cu 预先适应培养物,评估了接种物历史的重要性。预先适应后,与未预先适应的培养物相比,在存在 Pb、Zn 和 Cu 的 IC50 时,培养物的比生长速率分别提高了 39 ± 11%、32 ± 7%和 28 ± 12%。此外,当将暴露于 Pb、Zn 和 Cu 的 MIC 的细胞收获、洗涤并重新接种到新鲜、无金属的培养基中时,它们生长,表明细胞仍然具有活力,几乎没有残留毒性。最后,金属氯化物比金属硫酸盐毒性更大,使用氯化钠或金属硫酸盐和氯化钠混合物的研究表明,这归因于金属和氯化物毒性的附加组合。

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