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1.
The carbazole degrading bacterium JS1 was isolated from carbazole polluted soil and identified as Sphingomonas sp. bacterium based on its 16S rDNA gene. The car gene cluster located in the genome of JS1 was isolated by PCR and its presence verified by Southern hybridization. Sequence analysis of the car gene cluster showed that the arrangement of elements in JS1 was different from that of Pseudomons sp. CA10 and Nocardioides aromaticivorans IC177, but car gene cluster and neighboring regions were nearly identical to that of Sphingomonas sp. KA1 and Sphingomonas sp.GTIN11. Each element of the car gene cluster was expressed in E. coli upon IPTG induction. The amount of CaBb protein expressed was higher than CarBa and the ratio of these two proteins was 1:1.5. CarC expression level was detected using anti-CarC antibody. The result showed that carbazole degrading proteins were induced by the substrate carbazole. The quantity of CarC at 0.5 mg/ml carbazole was five times more than that at 0.1 mg/ml. Meiying Yang and Wenming Li have the equal contribution for this work.  相似文献   

2.
A hydrocarbon degrading and biosurfactant producing, strain DHT2, was isolated from oil-contaminated soil. The organism grew and produced biosurfactant when cultured in variety of substrates at salinities up to 6 g l−1 and temperatures up to 45°C. It was capable of utilizing crude oil, fuels, alkanes and PAHs as carbon source across the wide range of temperature (30–45°C) and salinity (0–6%). Over the range evaluated, the salinity and temperature did not influence the degradation of hydrocarbon and biosurfactant productions. Isolate DHT2 was identified as Pseudomonas aeruginosa by analysis of 16S rRNA sequences (100% homology) and biochemical analysis. PCR and DNA hybridization studies revealed that enzymes involved in PAH metabolism were related to the naphthalene dioxygenase pathway. Observation of both tensio-active and emulsifying activities indicated that biosurfactants were produced by DHT2 during growth on both, water miscible and immiscible substrates, including PAH. The biosurfactants lowered the surface tension of medium from 54.9 to 30.2 dN/cm and formed a stable emulsion. The biosurfactant produced by the organism emulsified a range of hydrocarbons with hexadecane as best substrate and toluene was the poorest. These findings further indicate that the isolate could be useful for bioremediation and bio-refining application in petroleum industry.  相似文献   

3.
A phenanthrene-mineralizing Pseudomonas sp., designated UG14, was isolated from creosote-contaminated soil. It contained two plasmids, of approximately 77 kb and 76 kb, the smaller of which contained DNA sequences that hybridized with probes specific for ndoB and xylE, genes involved in catabolism of aromatic hydrocarbons. At initial phenanthrene concentrations of 10, 50, 200 and 1000 mg/l broth, 27%, 19%, 7.7% and 3.3%, respectively, of the [9-14C]phenanthrene was recovered as 14CO2 after 36 days' incubation at 30°C. Most 14C-label was converted to a water-soluble metabolite tentatively identified as 1-hydroxy-2-naphthoic acid. Rhamnolipid biosurfactants produced by P. aeruginosa UG2 enhanced mineralization of 50 mg phenanthrene/l by Pseudomonas sp. UG14. With the biosurfactant at 0, 25 and 250 mg rhamnose equivalents/l, 6.5%, 8.2% and 9.8%, respectively, of the phenanthrene was mineralized after 35 days.M.A. Providenti, H. Lee and J.T. Trevors are with the Department of Environmental Biology, University of Guelph, Guelph, Ontario, N1G 2W1, Canada; C.W. Greer is with the National Research Council Canada, Biotechnology Research Institute, 6100 Royalmount Ave, Montreal, Quebec, H4P 2R2, Canada.  相似文献   

4.
Pseudomonas sp. strain LP1, an organism isolated on the basis of its ability to grow on pyrene, was assayed for its degradative and biosurfactant production potentials when growing on crude, diesel and engine oils. The isolate exhibited specific growth rate and doubling time of 0.304 days−1 and 2.28 days, respectively on crude oil (Escravos Light). The corresponding values on diesel were 0.233 days−1 and 2.97 days, while on engine oil, were 0.122 days−1 and 5.71 days. The organism did not show significant biosurfactant production towards crude oil and diesel, but readily produced biosurfactant on engine oil. The highest Emulsification index (E24) value for the biosurfactant produced by LP1 on engine oil was 80.33 ± 1.20, on day 8 of incubation. Biosurfactant production was growth-associated. The surface-active compound which exhibited zero saline tolerance had its optimal activity at 50°C and pH 2.0.  相似文献   

5.
A Pseudomonas sp. strain, CP4, was isolated that used phenol up to 1.5 g/l as sole source of carbon and energy. Optimal growth on 1.5 g phenol/l was at pH 6.5 to 7.0 and 30°C. Unadapted cells needed 72 h to decrease the chemical oxygen demand (COD) of about 2000 mg/l (from 1 g phenol/l) to about 200 mg/l. Adapted cells, pregrown on phenol, required only 65 h to decrease the COD level to below 100 mg/l. Adaptation of cells to phenol also improved the degradation of cresols. Cell-free extracts of strain CP4 grown on phenol or o-, m- or p-cresol had sp. act. of 0.82, 0.35, 0.54 and 0.32 units of catechol 2,3-dioxygenase and 0.06, 0.05, 0.05 and 0.03 units of catechol 1,2-dioxygenase, respectively. Cells grown on glucose or succinate had neither activity. Benzoate and all isomers of cresol, creosote, hydroxybenzoates, catechol and methyl catechol were utilized by strain CP4. No chloroaromatic was degraded, either as sole substrate or as co-substrate.The authors are with the Department of Microbiology and Bioengineering, Central Food Technological Research Institute, Mysore-570 013, India  相似文献   

6.
The range of substituted naphthalenesulfonates which are metabolized by Pseudomonas sp. BN6 were investigated. Resting cells from strain BN6 oxidized 1- and 2-naphthalenesulfonate, 1-hydroxynaphthalene-2-sulfonate, 2,6-naphthalenedisulfonate and all monosulfonated naphthalene-2-sulfonates which carry one or two substitutents in the positions 4-, 5-, 6-, 7- or 8- of the naphthalene ring-system. With the exception of (substituted) 4- or 5-amino- and 4-hydroxynaphthalene-2-sulfonates these compounds were converted to the corresponding salicylates. Strain BN6 did not oxidize substituted naphthalene-1-sulfonates, 3-substituted naphthalenesulfonates and substituted naphthalenedisulfonates. Turnover of 4-amino- or 4-hydroxynaphthalene-2-sulfonates resulted in the accumulation of the corresponding naphthoquinones in the culture medium. Thus, degradation of 4-amino- and 4-hydroxynaphthalenesulfonates was restricted by the rapid autoxidation of the substituted 1,2-dihydroxynaphthalenes formed as metabolites. Catabolic activities of strain BN6 for naphthalenesulfonates were induced by salicylate, 3- or 6-hydroxysalicylate, and 3-, 4- or 5-aminosalicylate but not by 4- and 5-hydroxysalicylate. All naphthalenesulfonates that were not converted into the corresponding salicylates, were found to be inefficient as effectors. It was therefore concluded that (substituted) salicylates are the inducers of the relevant enzymes. The degradation of 2-naphthalene-sulfonate by a pure culture of strain BN6 was prevented by the toxicity of the dead-end product salicylate. Substituted salicylates were less toxic and allowed growth of strain BN6 in axenic culture with various substituted naphthalenesulfonates.Abbreviations AB aminobenzoate - ANS aminonaphthalenesulfonate - DHN dihydroxynaphthalene - DHNC dihydroxynaphthalene-carboxylate - DHNDO 1,2-dihydroxynaphthalene dioxygenase - HBPA 2-hydroxybenzalpyruvate aldolase - HNS hydroxynaphthalenesulfonate - HS hydroxysalicylate - Ind-C indolecarboxylate - Ind-S indolesulfonate - MANS N-methylaminonaphthalenesulfonate - NC naphthalenecarboxylate - NDS naphthalenedisulfonate - NQ naphthoquinone - NS naphthalenesulfonate - NSDO naphthalenesulfonate dioxygenase - Rt retention time - SADH salicylaldehyde dehydrogenase - THN trihydroxynaphthalene (hydroxy-1,2-dihydroxynaphthalene)  相似文献   

7.
A soil bacterium SW4, capable of degrading the sulfonylurea herbicide ethametsulfuron-methyl (ESM), was isolated from the bottom soil of a herbicide factory. Based on physiological characteristics, biochemical tests and phylogenetic analysis of the 16S rRNA gene sequence, the strain was identified as a Pseudomonas sp. The total degradation of ESM in the medium containing glucose was up to 84.6% after 6 days of inoculation with SW4 strain. The inoculation of strain SW4 to soil treated with ESM resulted in a higher degradation rate than in noninoculated soil regardless of the soil sterilized or nonsterilized. Five metabolites of ESM degradation were analyzed by liquid chromatography/mass spectrometry. Based on the identified products, strain SW4 seemed to degrade ESM after two separate and different pathways: one leads to the cleavage of the sulfonylurea bridge, whereas the other to the dealkylation and opening of the triazine ring of ESM.  相似文献   

8.
A bacterium capable of degrading propoxur (2-isopropoxyphenyl-N-methylcarbamate) was isolated from soil by enrichment cultures and was identified as a Pseudomonas species. The organism grew on propoxur at 2 g/l as sole source of carbon and nitrogen, and accumulated 2-isopropoxyphenol as metabolite in the culture medium. The cell free extract of Pseudomonas sp. grown on propoxur contained the activity of propoxur hydrolase. The results suggest that the organism degraded propoxur by hydrolysis to yield 2-isopropoxyphenol and methylamine, which was further utilized as carbon source.  相似文献   

9.
A Pseudomonas sp. degraded benzalphthalide to o-phthalate and benzoate. A tentative pathway for the metabolism of benzalphthalide in this Pseudomonas sp. is proposed on the basis of isolated metabolites, oxygraphic assay and enzymatic studies.  相似文献   

10.
Pseudomonas sp. strain IST103 obtained from a stable consortium was capable of degrading pentachlorophenol (PCP) as sole carbon and energy source. The PCP-degrading potentiality of the strain was determined by growth of bacteria in culture medium, utilization of PCP by high performance liquid chromatography (HPLC), chloride release and ring cleavage. The strain was applied in two set of soil microcosms containing 20 and 40% moisture, each having different concentrations, 0, 10, 100, 500, and 1000 mg/l, of PCP. The result showed significant utilization of PCP (77% in 45 days) and higher growth of bacterial strain when PCP was applied in 100 mg/l concentration at 40% moisture. Inhibitory effects on the growth of bacterial strain were seen in 500 and 1000 mg/l concentration.  相似文献   

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