KR930012101B1 - New microorganism for digestion of polyvinyl alcohol - Google Patents
New microorganism for digestion of polyvinyl alcohol Download PDFInfo
- Publication number
- KR930012101B1 KR930012101B1 KR1019910016754A KR910016754A KR930012101B1 KR 930012101 B1 KR930012101 B1 KR 930012101B1 KR 1019910016754 A KR1019910016754 A KR 1019910016754A KR 910016754 A KR910016754 A KR 910016754A KR 930012101 B1 KR930012101 B1 KR 930012101B1
- Authority
- KR
- South Korea
- Prior art keywords
- pva
- pseudomonas
- polyvinyl alcohol
- strains
- kctc
- Prior art date
Links
Classifications
-
- C—CHEMISTRY; METALLURGY
- C12—BIOCHEMISTRY; BEER; SPIRITS; WINE; VINEGAR; MICROBIOLOGY; ENZYMOLOGY; MUTATION OR GENETIC ENGINEERING
- C12N—MICROORGANISMS OR ENZYMES; COMPOSITIONS THEREOF; PROPAGATING, PRESERVING, OR MAINTAINING MICROORGANISMS; MUTATION OR GENETIC ENGINEERING; CULTURE MEDIA
- C12N1/00—Microorganisms, e.g. protozoa; Compositions thereof; Processes of propagating, maintaining or preserving microorganisms or compositions thereof; Processes of preparing or isolating a composition containing a microorganism; Culture media therefor
- C12N1/20—Bacteria; Culture media therefor
Landscapes
- Life Sciences & Earth Sciences (AREA)
- Chemical & Material Sciences (AREA)
- Engineering & Computer Science (AREA)
- Health & Medical Sciences (AREA)
- Genetics & Genomics (AREA)
- Biotechnology (AREA)
- Organic Chemistry (AREA)
- Zoology (AREA)
- Bioinformatics & Cheminformatics (AREA)
- Wood Science & Technology (AREA)
- Medicinal Chemistry (AREA)
- Microbiology (AREA)
- Biomedical Technology (AREA)
- Virology (AREA)
- Biochemistry (AREA)
- General Engineering & Computer Science (AREA)
- General Health & Medical Sciences (AREA)
- Tropical Medicine & Parasitology (AREA)
- Purification Treatments By Anaerobic Or Anaerobic And Aerobic Bacteria Or Animals (AREA)
- Micro-Organisms Or Cultivation Processes Thereof (AREA)
Abstract
Description
제1도는 PVA 자화균 G5Y(KCTC-0020 BP)와 PW(KCTC-0021 BP)단독배양과 혼합배양시 각각의 성장력과 PVA 분해력을 나타낸 그라프.1 is a graph showing the growth and PVA degradability of each of the PVA magnetizing bacteria G5Y (KCTC-0020 BP) and PW (KCTC-0021 BP) culture alone and mixed culture.
제2도는 분리된 혼합균의 PVA 분해에 미치는 온도에 따른 영향을 나타낸 그라프.2 is a graph showing the effect of temperature on the PVA degradation of isolated mixed bacteria.
제3도는 분리된 혼합균의 PVA 분해에 미치는 PH 변화에 따른 영향을 나타낸 그라프.3 is a graph showing the effect of the pH change on the PVA degradation of isolated mixed bacteria.
제4도는 본 발명의 PVA 자화균주 Pseudomonas sp. G5Y 균주의 투과전자현미경 사진(배율 : 30,000배).4 is a PVA magnetizing strain Pseudomonas sp. Transmission electron micrograph of G5Y strain (magnification: 30,000 times).
제5도는 본 발명의 PVA 자화균주 Pseudomonas sp. PW 균주의 투과전자현미경 사진(배율 : 30,000배).5 is a PVA magnetizing strain Pseudomonas sp. Transmission electron micrograph of PW strain (magnification: 30,000 times).
제6도는 PVA 자화균주 Pseudomonas sp. G5Y와 Pseudomonas sp. PW의 혼합균주(KCTC 0022 BP)배양에 의한 PVA 분해력을 나타낸 그라프.6 shows Pseudomonas sp. G5Y and Pseudomonas sp. Graph showing PVA resolution by culture of mixed strain of PW (KCTC 0022 BP).
제7도는 스즈키(SUZUKI)등에 의해 분리된 PVA 자화균주의 PVA분해력을 나타낸 그라프.FIG. 7 is a graph showing PVA degradability of PVA magnetized strains separated by Suzuki et al.
제8도는 PVA 자화균주에 의한 실폐수중의 PVA 분해력을 나타낸 단면도.8 is a cross-sectional view showing PVA decomposition force in wastewater by PVA magnetizing strains.
본 발명은 풀리비닐알코올(Polyvinyl alcohol : PVA, 이하 PVA라함.)을 탄소원으로 하여 PVA를 강력하게 자화(資化)하는 미생물을 자연에서 분리한후 돌연변이를 유발한 변이주를 이용하여 폐수를 처리하는데 이용하고자 함에 있다.The present invention is to use the polyvinyl alcohol (PVA, hereinafter called PVA) as a carbon source to separate the microorganisms that strongly magnetize PVA in nature and to treat wastewater using the mutant strains causing mutations. To use.
일반적으로 자연계에서 각종 오염물질의 처리 및 분해균주가 분리, 동정되었는데 세균의 경우 슈도모나스속(Pseudomonas sp)이 상당한 부분을 차지하고 있다. 또한 하폐수 처리효율을 증진시키기 위하여 미생물 처리제도 개발되어 시판되고 있는데 이들 제품은 대부분이 자연계에서 분리된 세균이나 변이주(mutants)를 이용하여 만든 제품으로 우리나라에서도 이들 외국제품을 수입하여 시판하고 있는 실전이다. 그러나 이와 같이 수입된 미생물 제제의 경우 폐하수의 특성의 외국과 다를 뿐만아니라 처리조건도 다른 우리나라에서 관용할 경우 100% 효과를 기대하기 곤란하다. 또한 외국에서 수입되는 미생물 제제의 경우 수송, 운반, 보관 등 장시간이 소요되므로 미생물의 활성이 크게 감소될 우려가 있다. 그러므로 본 발명은 우리실정에 알맞은 폐수처리를 위한 미생물 처리제제와 고활성 균주를 개발하여 실용화하는데 있다.In general, the treatment and degradation strains of various pollutants have been isolated and identified in nature. Pseudomonas sp is a large part of bacteria. In addition, microbial treatment systems have been developed and marketed to improve the efficiency of wastewater treatment. Most of these products are made using bacteria or mutants isolated from nature. These products are imported from Korea and marketed in Korea. . However, in the case of the imported microbial preparations, it is difficult to expect 100% effect if the treatment conditions are different from those of other countries as well as the characteristics of wastewater. In addition, since the microbial agent imported from abroad takes a long time, such as transportation, transport, storage, there is a fear that the activity of the microorganism is greatly reduced. Therefore, the present invention is to develop and apply microbial treatment agent and high activity strain for wastewater treatment suitable for our situation.
염색가공 공장폐수에는 생물학적으로 난분해성 물질인 PVA를 다량함유하고 있는데, 이 들 PVA는 합성 섬유 비닐론의 원료로 널리 사용되고 있지만, 수용성인 상태로 용도가 개발되어 현재 섬유용 이외에도 풀먹이기용(Sizing), 접착제, 필름, 종이가공제등에 널리 사용되고 있다.Wastewater from dyeing and processing plants contains a large amount of PVA, a biologically hardly degradable substance. These PVAs are widely used as raw materials for synthetic fiber vinylon, but they have been developed in a water-soluble state and are currently used for grass feeding in addition to textiles. It is widely used in adhesives, films, and paper processing agents.
현재 대부분의 염색폐수 처리장에 사용되고 있는 활성오니법으로는 PVA 분해에 요구되는 시간만큼 체류시간을 유지할 수 없기 때문에 상당한 어려움이 많다. 또한, 오존산화법은 시설비 및 운영경비의 문제점이 많아 현실적으로 PVA 폐수 처리에는 어려움이 많다.Currently, the activated sludge method used in most dyeing wastewater treatment plants has a considerable difficulty because the residence time cannot be maintained for the time required for PVA decomposition. In addition, the ozone oxidation method has a lot of problems in the facility cost and operating costs, and in reality, the PVA wastewater treatment is difficult.
이와 같은 문제점을 해결하기 위해서는 공정의 개선이나 PVA를 단시일내에 분해할 수 있는 새로운 균주의 분리를 통해서만 가능하다.In order to solve this problem, it is possible only through improvement of the process or isolation of a new strain that can degrade PVA in a short time.
따라서 본 발명은 PVA를 단시일내에 분해하여 이들 분해물을 영양원으로하여 자화할 수 있는 우수한 미생물 균주를 분리한후 돌연변이를 유발한 변이주를 배양하여 PVA 폐수에 투입하여 경제적으로 저렴하게 PVA 폐수를 처리하는 것을 목적으로 하여 PVA 자화균의 분리를 실시하였다. 본 발명에 PVA 자화균의 분리는 다음과 같이 행하여졌다.Therefore, the present invention is to isolate PVA in a short time, isolate the excellent microbial strain that can be magnetized by using these degradation products as a nutrient source, and then culture the mutant-induced mutations and put them into PVA wastewater to treat PVA wastewater at low cost economically. PVA magnetization was isolated for the purpose. Separation of PVA magnetized bacteria in the present invention was carried out as follows.
먼저 PVA가 함유된 폐수처리장 주위의 하천수와 토양시료를 채취하여 이것을 시료원으로 사용하였다. 이 시료중 하천수와 토양을 멸균된 증류수로 현탁한 후 상등액 0.1ml씩을 표 1에 나타낸 배지에 1.5% 한천을 첨가한 고체의 평판배지에 도말하여 30℃에서 배양한 후 여기서 균집락을 순수분리하여 PVA 분해능이 우수한 균주를 선별하였다. 이때 PVA의 분해능 조사는 Finley 방법에 준하여 행하였다. 분리된 균주중 최종적으로 PVA 분해능이 우수한 균주를 선별한 후 N.T.C.(Nitronitroso Guaine)처리를 하여 슈도모나스 G5Y와 PW 두균주를 선별하였는데 이들 슈도모나스 G5Y와 PW는 단독 배양할 경우 PVA 분해율이 14% 내지 25%가 제거되었다. 또한 이 두 균주를 혼합하였을 때 90%이상 PVA가 제거되었다.(제1도). 이는 이들 두 균주(G5Y,PW)는 공생관계에 의해서 PVA를 제거하는 것으로 확인되었다 분리되어 돌연변이 처리된 상기 슈도모나스 균주 G5Y는 KCTC-0020BP호로, 슈도모나스 PW는 KCTC-0021BP호로 기탁되었다. 또한 혼합균주인 슈도모나스 G5Y와 PW는 KCTC-0022BP호로 기탁되었다. 본 분리균이 PVA를 분해하는데 미치는 생육특성중 온도의 영향을 조사한 결과는 제2도와 같다. 균의 배양온도를 25℃에서 40℃로 단계적으로 조절하여 표 1의 액체 배지에서 6일간 배양시킨 후 각 온도에서 균의 성장력과 PVA 제거물을 조사한 결과 30℃ 내지 35℃에서 균의 성장력이나 PVA 제거율이 우수하였으며 최적온도는 35℃로 나타났다. 배지의 최적 PH를 결정하기 위해서 배양온도를 35℃에서 PH를 5.0 내지 9.0까지 단계적으로 조절하여 균의 성장력과 PVA분해율을 조사한 결과는 제3도와 같다.First, river water and soil samples around the wastewater treatment plant containing PVA were collected and used as the sample source. Suspension of the river water and soil in this sample with sterile distilled water, 0.1 ml each of the supernatant was plated on a solid plate medium with 1.5% agar added to the medium shown in Table 1 and incubated at 30 ° C. Strains with good PVA resolution were selected. At this time, the resolution investigation of PVA was performed according to the Finley method. Among the isolated strains, strains with excellent PVA resolution were selected and then Pseudomonas G5Y and PW two strains were selected by NTC treatment (Nitronitroso Guaine). Was removed. In addition, when the two strains were mixed, more than 90% of PVA was removed (FIG. 1). These two strains (G5Y, PW) was confirmed to remove the PVA by a symbiotic relationship. The isolated and mutated Pseudomonas strain G5Y was deposited as KCTC-0020BP, Pseudomonas PW as KCTC-0021BP. In addition, Pseudomonas G5Y and PW mixed strains were deposited with KCTC-0022BP. The results of investigation of the effect of temperature on the growth characteristics of the isolates on PVA degradation are shown in FIG. After culturing the culture temperature of bacteria in 25 ° C to 40 ℃ stepwise incubated for 6 days in the liquid medium of Table 1, the growth power and PVA removal of the bacteria at each temperature was examined and the growth power or PVA at 30 ℃ to 35 ℃ The removal rate was excellent and the optimum temperature was 35 ℃. In order to determine the optimal pH of the medium, the growth temperature and PVA degradation rate of the bacteria were examined by controlling the culture temperature at 35 ° C. in steps of 5.0 to 9.0.
제3도엔 나타난 바와 같이 PH6.5 이하에서는 균의 성장력이나 PVA 제거율이 미약하였지만 PH6.5 이상의 범위에서는 양호한 결과를 나타내었으며 최적 PH는 7.5로 나타났다.As shown in FIG. 3, the growth rate and the PVA removal rate of bacteria were weak at pH 6.5 and below, but showed good results at pH 6.5 and above, and the optimum pH was 7.5.
또한 균의 동정을 위하여 여러 가지 형태적, 생리적, 화학적 자료를 조사한 결과 표 2, 제4도, 제5도와 같은 자료를 산출하였다.In addition, various morphological, physiological and chemical data were examined for the identification of bacteria, and the data shown in Table 2, 4, and 5 were calculated.
이 자료를 근거로 하여 균을 동정한 결과 각 슈도모나스 세파시아(Pseudomonas cepacia)와 슈도모나스 슈도말레이(Pseudomonas pseudomallei)의 유사균으로 동정이 되어 이들을 각각 Pseudomonas sp. G5Y, Pseumonas sp. PW로 명명하였다.Based on these data, the bacteria were identified as Pseudomonas cepacia and Pseudomonas pseudomallei, respectively, and these were identified as Pseudomonas sp. G5Y, Pseumonas sp. Named PW.
제6도에 표 시한 것과 같이 250ml 삼각플라스크에 1L당 5g의 PVA을 함유한 배지 100ml를 넣고 이것의 10% 해당하는 PVA 자화균을 접종하여 35℃에서 180RPM으로 회전진탕 배양하여 PVA 분해능을 측정한 결과 이들 혼합균주들의 PVA 분해능은 매우 우수하여 3일 이내에 90%이상 분해할 수 있었다.As shown in FIG. 6, 100 ml of medium containing 5 g of PVA per 1L was inoculated into a 250 ml Erlenmeyer flask, and 10% of this was inoculated with PVA magnetizing bacteria. As a result, the PVA resolution of these mixed strains was very good and could decompose more than 90% within 3 days.
이결과는 기존의 스즈키(SUZUKI)등이 분리한 균주가 90%이상 PVA를 분해하는데 4일이상 소요된 것에 비하여 우수한 성적이라 할 수 있다(제7도).This result can be said to be excellent results compared to the conventional strain Suzuki (SUZUKI, etc.) took more than 4 days to break down PVA more than 90% (Fig. 7).
또한 실제호발폐수(PVA함유 폐수)에서 PVA 분해능을 조사하기 위하여 D도시 D방적의 PVA 함유폐수에 본 발명 균주를 접종하여 PVA 분해능을 조사한 결과는 제8도와 같다. 실제호발폐수의 PVA 농도를 5000mg/l, BOD:N:P=100:5:1로 조정하여 3일간 배양한 결과 약 75% 정도의 PVA가 제거되어 실 폐수에서도 PVA를 빠른 시간내에 제거함이 나타났다. 이와 같이 본 발명에서 분리한 PVA 자화균 Pseudomonas sp G5Y와 Pseudomonas sp. PW 균주를 혼합배양시 PVA 분해 자화능이 우수하였으며 실제폐수처리장에서도 경제적으로 PVA를 제거할 수 있는 우수한 균주로 사료된다.In addition, in order to investigate the PVA resolution in the actual call wastewater (PVA-containing wastewater), the strain of the present invention was inoculated to the PVA-containing wastewater in D-D spinning, and the PVA resolution was examined as shown in FIG. After 3 days of incubation with PVA concentration of 5000mg / l and BOD: N: P = 100: 5: 1, it was found that about 75% of PVA was removed and PVA was removed quickly in real wastewater. . As described above, PVA magnetizing bacteria Pseudomonas sp G5Y and Pseudomonas sp. When PW strains were mixed in culture, PVA decomposed magnetization was excellent, and it is considered to be an excellent strain that can economically remove PVA even in actual wastewater treatment plant.
[표 1]TABLE 1
[표 2]TABLE 2
Claims (4)
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
KR1019910016754A KR930012101B1 (en) | 1991-09-26 | 1991-09-26 | New microorganism for digestion of polyvinyl alcohol |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
KR1019910016754A KR930012101B1 (en) | 1991-09-26 | 1991-09-26 | New microorganism for digestion of polyvinyl alcohol |
Publications (2)
Publication Number | Publication Date |
---|---|
KR930006149A KR930006149A (en) | 1993-04-20 |
KR930012101B1 true KR930012101B1 (en) | 1993-12-24 |
Family
ID=19320350
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
KR1019910016754A KR930012101B1 (en) | 1991-09-26 | 1991-09-26 | New microorganism for digestion of polyvinyl alcohol |
Country Status (1)
Country | Link |
---|---|
KR (1) | KR930012101B1 (en) |
Cited By (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
KR100384518B1 (en) * | 1998-11-06 | 2003-08-19 | 공경석 | An undrewater fluorescent lamp |
-
1991
- 1991-09-26 KR KR1019910016754A patent/KR930012101B1/en not_active IP Right Cessation
Cited By (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
KR100384518B1 (en) * | 1998-11-06 | 2003-08-19 | 공경석 | An undrewater fluorescent lamp |
Also Published As
Publication number | Publication date |
---|---|
KR930006149A (en) | 1993-04-20 |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
US3940332A (en) | Treating waste water containing nitriles and cyanides | |
Baross et al. | Survival of human enteric and other sewage microorganisms under simulated deep-sea conditions | |
DE69320938T2 (en) | Process for the biodegradation of trichloroethylene and dichloroethylene and for soil remediation by microorganisms Pseudomonas cepacia KKO1 (FERM BP-4235) | |
US4855051A (en) | Microbial treatment of wastewater to remove tertiary butyl alcohol | |
Ueda et al. | Microflora of activated sludge | |
Bux, F* & Kasan | A microbiological survey of ten activated sludge plants | |
IE71193B1 (en) | Methods for the biological inactivation of nucleic acids | |
EP1204608A2 (en) | Method of purifying water, suitable bacteria for the method and use thereof | |
KR930012101B1 (en) | New microorganism for digestion of polyvinyl alcohol | |
Sugiura et al. | Grazing characteristics of musty-odor-compound-producing Phormidium tenue by a microflagellate, Monas guttula | |
Kataoka et al. | Enrichment culture and isolation of slow-growing bacteria | |
KR19980033946A (en) | Active microorganism culture material for wastewater treatment and its use method | |
JPH0622769A (en) | Method for biodegradation of phenolic compound, new strain used therefor and method for obtaining microorganism having ability to degrade phenolic compound | |
Williams et al. | Environmental distribution of Zoogloea strains | |
JP5046665B2 (en) | Novel microorganism and drainage purification method using the same | |
US3634226A (en) | Biochemical process | |
CN111205997B (en) | Bacillus methylicus and application thereof in degrading micro-pollutants in environment | |
JPH06106198A (en) | Method and device for microbiological reduction of amount of surplus sludge | |
KR100443666B1 (en) | A Novel Microorganism Capable of Digesting Polyacrylic Acid Ester, and A Method of Treating Wastewater Using the Same | |
KR100350928B1 (en) | Klebsiella pneumoniae CJ-PVA a), Pseudomonas putida CJ-PVA b) and Pseudomonas putida CJ-PVA c) having an improved property for degrading polyvinylalcohol | |
JP3507151B2 (en) | Biodegradation method of halogen-substituted organic acids and novel microorganisms used therefor | |
Kuruvila et al. | A Study on the Microbial Processing of Natural Rubber Wastewater Effluent From a Rubber Processing Unit | |
JP2869838B2 (en) | Degradation method of aliphatic polyester using anaerobic bacteria | |
JPH09234060A (en) | New microorganism | |
Shimizu et al. | Improvement of settling characteristics of activated sludge by addition of a floc-forming bacterium |
Legal Events
Date | Code | Title | Description |
---|---|---|---|
A201 | Request for examination | ||
E902 | Notification of reason for refusal | ||
G160 | Decision to publish patent application | ||
E701 | Decision to grant or registration of patent right | ||
GRNT | Written decision to grant | ||
FPAY | Annual fee payment |
Payment date: 19971127 Year of fee payment: 5 |
|
LAPS | Lapse due to unpaid annual fee |