首页> 外文会议>International Biohydrometallurgy Symposium, IBS-2001 Sep 16-19, 2001, Ouro Preto, Minas Gerais, Brazil >Biotechnological neutralization of cyanides and thiocyanates in cyanidation tails of gold ores and concentrates
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Biotechnological neutralization of cyanides and thiocyanates in cyanidation tails of gold ores and concentrates

机译:金矿石和精矿氰化尾矿中氰化物和硫氰酸盐的生物技术中和

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摘要

The role played by a bacterial community composed of Pseudomonasputida, strain 21; Pseudomonas stutzeri, strain 18; and Pseudomonas sp., strain 5, and by physical and chemical factors in the degradation of CN~- and SCN~- was studied. It was shown that the degradation of CN~- is determined both by the action of bacteria and by abiotic physical and chemical factors (pH, O_2, temperature, the medium agitation rate, etc.). The contribution of chemical degradation was found to increase drastically at pH below 9.0; when air was blown through the medium (irrespective of the pH value); under active agitation of the medium; and when the medium surface interfacing air was increased. Even at elevated pH values (9.0-9.2), suboptimal for bacterial growth, the microbial degradation could account for at most 20-25 mg/l of CN~-, regardless of its initial concentration. When CN~- or SCN~- were concurrently present in the medium or in the pulp, the former compound was the first to be degraded by microorganisms. CN~- and SCN~- were utilized by bacteria solely as nitrogen sources. The detoxification of cyanide-containing pulps could be achieved by the combination of chemical degradation of cyanide, resulting in the decrease of its concentration, and the subsequent oxidation of SCN~- and the residual CN~- by a community of heterotrophic bacteria.
机译:由假单胞假单胞菌21株组成的细菌群落发挥的作用; Stutzeri假单胞菌,菌株18;并通过理化因素研究了菌株5和假单胞菌属菌株Pseudomonas sp。的降解情况。结果表明,CN_-的降解是由细菌的作用和非生物的理化因素(pH,O_2,温度,培养基搅拌速率等)共同决定的。发现在pH值低于9.0时,化学降解的作用急剧增加。当空气吹过介质时(与pH值无关);在介质的积极搅拌下;当介质表面界面空气增加时。即使在升高的pH值(9.0-9.2)下(对于细菌生长而言不是最理想的),无论其初始浓度如何,微生物降解都可能占至多20-25 mg / l的CN〜-。当CN_-或SCN_-同时存在于培养基或果肉中时,前一种化合物最先被微生物降解。细菌利用CN〜-和SCN〜-作为氮源。含氰化物纸浆的解毒可以通过氰化物化学降解,降低其浓度以及随后由异养细菌群落氧化SCN〜-和残留CN〜-来实现。

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