• KSBB Journal
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• v.18 no.6
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• pp.479-484
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• 2003

34 strains were isolated from dyeing wastewater in order to improve treatment efficiency of dyeing wastewater containing PVA. Two strains of them were finally selected through the PVA degrading test, and identified as Microbacterium barkeri LCa and Paenibacillus amylolyticus LCb. As a result, optimal conditions for microbial growth and PVA degradation were 30$^{\circ}C$, neutral pH, starch as a carbon source, and peptone as a nitrogen source. And it was concluded that these two strains have good ability for PVA degradation. And 90% over PVA was degraded by single culture as well as a mixed culture of 2 different strains.

• KSBB Journal
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• v.21 no.1 s.96
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• pp.54-58
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• 2006

The purpose of this study is to search the characteristics of PVA degrading enzymes which were obtained from Microbacterium barkeri KCCM 10507 and Paenibacillus amylolyticus KCCM 10508, respectively. As a result of the PVA degrading test using crude enzymes, the activity of SAO (secondary alcohol oxidase) was maximized after 2 or 3 days from start of the test, while the activity of BDH (${\beta}$-diketone hydrolase) was gradually increased during the test. Activities of them were maintained in the presence of PVA, but as PVA was gradually degraded, their activity was decreased. PVA was inoculated again into the media, their activity was revealed. This result indicated that above two different enzymes were closely connected with PVA degradation and PVA was degraded by activity of SAO and BDH. Maximum activity of them was 1.5-1.8 unit for SAO and 1.5-2.0 unit for BDH under $35^{\circ}C$ and pH 7.8-8.8, respectively.

• Journal of Microbiology and Biotechnology
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• v.14 no.5
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• pp.1009-1013
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• 2004

The purpose of this study was to investigate the degradation of PVA (polyvinyl alcohol) contained in dyeing wastewater by a mixed culture of Microbacterium barkeri KCCM 10507 and Paenibacillus amylolyticus KCCM 10508. Firstly, synthetic wastewater which contained different initial concentrations of PVA varying from 50 to 3,500 mg/l were tested to obtain optimal PVA biodegradation activity of isolated strains, and the above two strains were found to degrade PVA up to 90%, when the initial concentration of PVA was 750 mg/l and below. Next, dyeing wastewater was tested by a nixed culture of the two isolated strains, and 42% and 55% of the initial concentrations of PVA and COD, respectively, was removed after five days. MLSS was gradually increased from an initial 1,400 to 2,500 mg/l, and the pH was also increased from 5.1 to 7.8. Sterilized dyeing wastewater was tested to find the effect of strains only on the biodegradation of PVA, and PVA degradation ratio and COD removal ratio were 50% and 72.8%, respectively. Thus, the results indicated that these two strains have good ability to degrade PVA and remove COD in dyeing wastewater, Finally, it is expected that if these two strains were used in the dyeing wastewater treatment, good efficiency for PVA degradation and COD removal could be achieved.

• 한국생물공학회:학술대회논문집
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• 2003.10a
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• pp.403-403
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• 2003

• 한국생물공학회:학술대회논문집
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• 2003.04a
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• pp.414-418
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• 2003

Through the PVA degrading test, 8 species of microbes were finally isolated, and two species among them were identified. To search PVA degrading rate by using 8 species of microbes, single species of microbes and combination of each species were tested. As a result, single species of microbes showed 96% of PVA degrading rate, and the similar result was obtained by using combination of two species. And 78% of PVA degrading rate was obtained by using enzyme which was secreted from good PVA degrading microbes. As a result of identification, this good PVA degrading microbes were Paenibacillus sp. and Microbacterium barkeri.

• KSBB Journal
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• v.19 no.5
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• pp.390-393
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• 2004

Oxygen uptake rate (OUR) was used as an indicator of microbial activity. In this study OUR at dyeing wastewater in the pilot plant was monitored to examine biological activity. Correlation between inlet COD concentration and maximum OUR showed that maximum OUR was proportional to inlet COD concentration. Changes in the OUR values reflected the changing waste load in the reactor. Consequently, OUR can be used to estimate biological activity of inlet COD concentration. This study showed that biodegradable COD at dyeing wastewater could be calculated from OUR and yield coefficient. Non-biodegradable COD was able to be calculated from a difference between initial COD concentration and biodegradable COD.