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Cyanide production by Pseudomonas fluorescens and Pseudomonas aeruginosa.

机译:荧光假单胞菌和铜绿假单胞菌产生氰化物。

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摘要

Of 200 water isolates screened, five strains of Pseudomonas fluorescens and one strain of Pseudomonas aeruginosa were cyanogenic. Maximum cyanogenesis by two strains of P. fluorescens in a defined growth medium occurred at 25 to 30 degrees C over a pH range of 6.6 to 8.9. Cyanide production per cell was optimum at 300 mM phosphate. A linear relationship was observed between cyanogenesis and the log of iron concentration over a range of 3 to 300 microM. The maximum rate of cyanide production occurred during the transition from exponential to stationary growth phase. Radioactive tracer experiments with [1-14C]glycine and [2-14C]glycine demonstrated that the cyanide carbon originates from the number 2 carbon of glycine for both P. fluorescens and P. aeruginosa. Cyanide production was not observed in raw industrial wastewater or in sterile wastewater inoculated with pure cultures of cyanogenic Pseudomonas strains. Cyanide was produced when wastewater was amended by the addition of components of the defined growth medium.
机译:在筛选的200个水分离株中,有5株荧光假单胞菌和1株绿脓杆菌是生氰的。在限定的生长培养基中,两株荧光假单胞菌的最大氰化作用发生在25至30摄氏度,pH范围为6.6至8.9。每个细胞的氰化物产量在300 mM磷酸盐时最佳。在3到300 microM的范围内,在生氰和铁浓度的对数之间观察到线性关系。氰化物生产的最大速率发生在从指数到平稳生长期的过渡过程中。用[1-14C]甘氨酸和[2-14C]甘氨酸进行的放射性示踪剂实验证明,对于碳荧光假单胞菌和铜绿假单胞菌,氰化物碳均来自甘氨酸的2号碳。在未经处理的工业废水中或在纯净的生氰假单胞菌菌株接种的无菌废水中均未观察到氰化物的产生。当通过添加确定的生长培养基的成分来修正废水时,会生成氰化物。

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