• Title/Summary/Keyword: Microbacterium laevaniformans

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Purification of Isocitrate lyase Produced from Microbacterium laevaniformans (Microbacterium laevaniformans가 생성하는 Isocitrate lyase의 정제)

  • 서승교;김정호
    • Journal of Environmental Science International
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    • v.7 no.6
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    • pp.853-857
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    • 1998
  • Purification of the isocitrate lyase extracted from Microbacterium laevaniformans was investigated. The isocitrate lyase was purified 43.6 folds by the following continuous treatment with ammonium sulfate fraction, DEAE-cellulose, DEAE-sephacel and Sephadex G-200 chromatography. The purified isocitrate lyase was showed to be a single protein band by polyacrylamide gel electrophoresis. The molecular weight of the purified isocitrate lyase was estimated 54,000 Da by the SDS-polyacrylamide gel electrophoresis. The Km and Vmax values for isocitrate were estimated to be 0.83mM and 0.33units/ml, respectively. Activity of isocitrate lyase was inhibited by cystein-HCl and glutathione.

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Action Mechanism of Transfructosylation Catalyzed by Microbacterium laevaniformans Levansucrase

  • KIM, MIN-JEONG;PARK, HAE-EUN;SUNG, HEE-KYUNG;PARK, TACK-HYUN;CHA, JAE-HO
    • Journal of Microbiology and Biotechnology
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    • v.15 no.1
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    • pp.99-104
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    • 2005
  • Microbacterium laevaniformans levansucrase synthesized various hetero-oligosaccharides by transferring fructosyl residue from sucrose to various saccharides as acceptors. The acceptor specificity test showed that reducing saccharides were more favorable acceptors than nonreducing saccharides. The transfructosylated product, fructosyl galactose, was produced in the presence of D-galactose as an acceptor. The chemical structure of the resulting fructosyl galactose was analyzed by yeast invertase and NMR, and identified as O-$\alpha$-D-galactosyl-(1${\to}$2)-$\beta$-D-fructofuranoside. These results indicate that the main transfructosylation activity of the enzyme is to make nonreducing transferred products via a transfer of fructosyl residue to acceptor molecules having reducing group. When nonreducing sugars, such as methyl $\alpha$-D-glucoside and methyl $\alpha$-D-galactoside, were used as an acceptor, the transfer product was also formed in spite of the reducing group blocked with methyl group. The fact that no transfer product was formed with sugar alcohols as acceptors was suggested to be due to marked conformational difference of acceptors.

Analysis of Waste Water and Isolation of Strains Assimilation Waste Water from Acetaldehyde Plant (아세트 알데히드(특수산업) 공장폐수의 성분과 이용균주의 분리)

  • 정기택;서승교;송형익;박임동;방광웅
    • Korean Journal of Microbiology
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    • v.25 no.4
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    • pp.328-332
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    • 1987
  • As a research for treatment of waste water from acetaldehyde plant by biological method, we investigated general characteristics of the waste water, and isolated and identified some useful bacteria which effectively treated its waste water. Among the total number of 53 strains which were grown in waste water from an acetaldehyde plant, the strains AW-6, AW-22, AW-38 and AW-41 were found to be useful for COD removal of waste water. $COD_{Mn}$ and $BOD_{5}$ of the waste water were 5260 ppm and 6452 ppm, respectively, and pH was 1.85. And the main organic component in waste water was acetic acid which was contained 6.76%. By the taxonomical characteristics, the strains AW-6, AW-22, AW-38 and AW-41 were identified as Micrococcus roseus, Micrococcus luteus, Microbacterium lacticum and Microbacterium laevanifromans or similar strain, respectively.

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Effects of Microbacterium laevaniformans Levans Molecular Weight on Cytotoxicity

  • Oh, Im-Kyung;Yoo, Sang-Ho;Bae, In-Young;Cha, Jae-Ho;Lee, Hyeon-Gyu
    • Journal of Microbiology and Biotechnology
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    • v.14 no.5
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    • pp.985-990
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    • 2004
  • Levans produced from Microbacterium laevaniformans were isolated, characterized, and fractionated by molecular weight. TLC, HPLC, and GC-MS analyses of the exopolysaccharide showed that it was a fructan-type polymer and was composed of (2,6)- and (2,1)-glycosidic linkages. $^{13}C$-NMR analysis proved that the polysaccharide was mainly a $\beta$-(2,6)-linked levan-type polysaccharide. To investigate the cytotoxicity of the acetone-precipitated levan fractions such as M1, M2, and M3, HepG2, P388D1, U937, SNU-1, and SNUC2A cell lines were screened. Among the cell lines tested, the cytotoxicity of M1- M3 fractions were detected from only SNU-1 and HepG2 cells at the dosage level of $100-800\mu\textrm{g}ml$. The M2 fraction M_r$, 80,000) at 400 $mu{g/ml}$ had the greatest cell growth inhibition (84.6%) on SNU-1, while the M1 $(M_r$, 50,000) at $800\mu\textrm{g}ml$ showed the greatest (46.32%) on HepG2. To obtain more uniform M_r$ fractions of levan, the levan was further fractionated from S1 $(M_r$ 1,000,000) to S5 $(M_r$ 10,000) using gel permeation chromatography. Again, the S1-S5 fractions had strong cytotoxicity on SNU-1 and HepG2 cell lines. The greatest inhibition effects of S4 $(M_r$ 80,000) on SNU-1 and S5 $(M_r$ 10,000) on HepG2 were shown to be 49.5% and 73.0%, respectively. The cytotoxicity of the levan fractions was more effective on SNU-1 than on HepG2. Although the relationship between the Mw and the cytotoxicity was not clear, smaller $M_r$, fractions of levan showed greater growth inhibition effect on the cancer cell lines in general. Therefore, it was indicated that a specific Mw class of levan is responsible for the effective cytotoxicity.

Disinfection Efficiency of Medium Pressure UV Lamp on Major Bacteria in Sand Filtered Water (사여과수에 존재하는 우점세균의 중압 자외선 램프 소독능)

  • Ahn, Seoung-Koo;Yang, Yoon-Yong
    • Journal of Korean Society of Environmental Engineers
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    • v.32 no.12
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    • pp.1141-1146
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    • 2010
  • Isolated the heterotrophic aerobic bacteria in sandfiltered water on NA and TSBA solid medium, selected 8 dominant species and identified by Sherlock System. Each samples are irradiated 0, 5, 16, 40 and $60\;mJ/cm^2$ using on CBD (Collimated Beam Device) Medium Pressure UV lamp after these identified bacterium did liquid culture how to make $10^6{\sim}10^7\;cells/mL$ suspended in dilution water. Then cultured bacteria are estimated inactivation rate on plate media. Identified Gram positive group are Bacillus Subtilus, Bacillus megaterium, Rhodococcus erythropolis and Microbacterium laevaniformans; Gram negative group are Pseudomonas vesicularis, Pseudomonas pseudoflava, Alcaligenes paradoxus and Zooglea ramigera. These isolation of bacterium are more stronger reference strain and high resistance of MP UV irradiation, Besides Gram negative bacterium are more sensitive Gram positive bacterium on MP UV dose. Now we are estimating to $60{\sim}100\;mJ/cm^2$ MP UV dose for efficient disinfection in water treatment plant.

Studies on the Biological Treatment of Waste Water from Acetaldehyde Plant (아세트 알데히드(특수산업) 폐수의 생물학적 처리)

  • 정기택;서승교;송형익;박임동;방광웅
    • Korean Journal of Microbiology
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    • v.25 no.4
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    • pp.333-338
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    • 1987
  • In order to establish the biological treatment system which can be used for treatment of waste aster from acetaldehyde plant, it was investigated optimum nutrient requirements and growth conditions by mixed culture of Micrococcus roseus AW-6, Micrococcus luteus AW-22, Microbacterium lacticum AW-38 and Microbacterium laevaniformans AW-41 as well as the effect of coagulants and neutralization reagents. Also, it was carried out the continuous culture as well as batch culture to treat the waste water by mixed culture of these strains. The COD removal rate was reached to maximum state for 96hrs culture at pH7.0 and $30^{\circ}C$ NaOH as the neutralization reagents was the most effective, but the coagulants had no effect on the COD remonal rate and the optimum dilution times for treatment were 10 fold. The COD removal rate was also increased by supplimenting 200 ppm $NH_{2}NO_{3}$, 50 ppm $KH_{2}PO_{4}$, 15 ppm $CaCl_{2}$ and 1 ppm $MgSO_{4} \cdot 7H_{2}O $ as additional nutrients. The removal rate coefficient $K_{1}$ on the batch culture was $4.5\times 10^{-6}$, and the detention time for BOD removal rate of 85% was approximately 45hrs. The COD of waste water was reduced to 15% of its initial value by the continuous culture. The COD and BOD of the effluents were to be about 60 ppm and 40 ppm, respectively, and final pH was 7.0.

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