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关于氯对黄铁矿生物氧化效率的毒性影响的研究。

A study on the toxic effects of chloride on the biooxidation efficiency of pyrite.

机构信息

Division of Extractive Metallurgy, Luleå University of Technology, SE-971 87 Luleå, Sweden.

出版信息

J Hazard Mater. 2009 Dec 30;172(2-3):1273-81. doi: 10.1016/j.jhazmat.2009.07.133. Epub 2009 Aug 7.

Abstract

Bioleaching operations in areas with limited chloride-free water and use of ashes and dust as neutralizing agents have motivated to study the chloride toxicity and tolerance level of the microorganisms. Biooxidation of pyrite using chloride containing waste ash compared with Ca(OH)(2)+NaCl as neutralizing agent was investigated to evaluate the causes of low pyrite oxidation. Both precipitation of jarosite as well as the toxic effect of chloride on the microorganisms were responsible for lower pyrite recoveries. Another study with sudden exposure of chloride during pyrite biooxidation, addition of 4 g/L was lethal for the microorganisms. Addition of 2g/L chloride resulted in precipitation of jarosite with slightly lower pyrite recovery whereas the addition of 3g/L chloride temporarily chocked the microorganisms but activity was regained after a short period of adaptation. Population dynamics study conducted on the experiment with 3g/L chloride surprisingly showed that Leptospirillum ferriphilum, which was dominating in the inoculum, completely disappeared from the culture already before chloride was added. Sulphobacillus sp. was responsible for iron oxidation in the experiment. Both Acidithiobacillus caldus and Sulphobacillus sp. were adaptive and robust in nature and their numbers were slightly affected after chloride addition. Therefore, it was concluded that the microbial species involved in the biooxidation of pyrite vary in population during the different stages of biooxidation.

摘要

在缺乏无氯水资源的地区进行生物浸出作业,并使用灰烬和粉尘作为中和剂,这促使人们研究微生物的氯化物毒性和耐受水平。本研究采用含氯化物的废灰作为中和剂进行生物氧化,与 Ca(OH) 2 + NaCl 进行对比,以评估黄铁矿氧化率低的原因。黄铁矿氧化率低的原因是一方面生成了铁矾,另一方面是氯化物对微生物有毒害作用。在黄铁矿生物氧化过程中突然暴露于氯化物的另一项研究中,添加 4 g/L 的氯化物对微生物是致命的。添加 2 g/L 的氯化物会导致铁矾沉淀,从而导致黄铁矿回收率略有下降,而添加 3 g/L 的氯化物会暂时抑制微生物的活性,但在适应短时间后活性会恢复。在添加 3 g/L 氯化物的实验中进行的种群动态研究令人惊讶地表明,在接种物中占主导地位的 Leptospirillum ferriphilum 已经在添加氯化物之前从培养物中完全消失。在实验中,Sulphobacillus sp. 负责铁的氧化。在氯化物添加后,两种嗜酸菌(Acidithiobacillus caldus 和 Sulphobacillus sp.)都具有适应性和强健性,其数量只有轻微变化。因此,可以得出结论,参与黄铁矿生物氧化的微生物在生物氧化的不同阶段在种群数量上存在差异。

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