KR20000056878A - Production of Pichia guilliermondii Biomass Using Saline Medium and Process for Treating Waste by Employing Same - Google Patents
Production of Pichia guilliermondii Biomass Using Saline Medium and Process for Treating Waste by Employing Same Download PDFInfo
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- KR20000056878A KR20000056878A KR1019990006620A KR19990006620A KR20000056878A KR 20000056878 A KR20000056878 A KR 20000056878A KR 1019990006620 A KR1019990006620 A KR 1019990006620A KR 19990006620 A KR19990006620 A KR 19990006620A KR 20000056878 A KR20000056878 A KR 20000056878A
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- FAPWRFPIFSIZLT-UHFFFAOYSA-M Sodium chloride Chemical compound [Na+].[Cl-] FAPWRFPIFSIZLT-UHFFFAOYSA-M 0.000 title claims abstract description 84
- 239000011780 sodium chloride Substances 0.000 title claims abstract description 45
- 241000235048 Meyerozyma guilliermondii Species 0.000 title claims abstract description 9
- 239000002699 waste material Substances 0.000 title claims description 62
- 238000004519 manufacturing process Methods 0.000 title claims description 50
- 238000000034 method Methods 0.000 title claims description 44
- 230000008569 process Effects 0.000 title description 12
- 239000002028 Biomass Substances 0.000 title 1
- 239000002351 wastewater Substances 0.000 claims abstract description 137
- 235000021109 kimchi Nutrition 0.000 claims abstract description 37
- 150000003839 salts Chemical class 0.000 claims abstract description 26
- 238000012258 culturing Methods 0.000 claims abstract description 15
- 240000007124 Brassica oleracea Species 0.000 claims description 33
- 235000003899 Brassica oleracea var acephala Nutrition 0.000 claims description 33
- 235000011301 Brassica oleracea var capitata Nutrition 0.000 claims description 33
- 235000001169 Brassica oleracea var oleracea Nutrition 0.000 claims description 33
- 235000010149 Brassica rapa subsp chinensis Nutrition 0.000 claims description 30
- 235000000536 Brassica rapa subsp pekinensis Nutrition 0.000 claims description 30
- 241000499436 Brassica rapa subsp. pekinensis Species 0.000 claims description 30
- 238000005554 pickling Methods 0.000 claims description 23
- 241000196324 Embryophyta Species 0.000 claims description 19
- 241000235648 Pichia Species 0.000 claims description 19
- 238000012545 processing Methods 0.000 claims description 15
- 235000011389 fruit/vegetable juice Nutrition 0.000 claims description 10
- 239000005416 organic matter Substances 0.000 claims description 8
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- 230000012010 growth Effects 0.000 abstract description 52
- 240000004808 Saccharomyces cerevisiae Species 0.000 abstract description 27
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- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Chemical compound O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 abstract description 9
- 238000004065 wastewater treatment Methods 0.000 abstract description 6
- 235000019750 Crude protein Nutrition 0.000 abstract description 4
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- 108090000623 proteins and genes Proteins 0.000 abstract description 2
- 102000004169 proteins and genes Human genes 0.000 abstract description 2
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- IJGRMHOSHXDMSA-UHFFFAOYSA-N Atomic nitrogen Chemical compound N#N IJGRMHOSHXDMSA-UHFFFAOYSA-N 0.000 description 10
- 235000013305 food Nutrition 0.000 description 9
- 241000222120 Candida <Saccharomycetales> Species 0.000 description 7
- 229910000368 zinc sulfate Inorganic materials 0.000 description 7
- 238000000855 fermentation Methods 0.000 description 6
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- 230000009467 reduction Effects 0.000 description 6
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- 238000004458 analytical method Methods 0.000 description 5
- 229910052757 nitrogen Inorganic materials 0.000 description 5
- 238000010561 standard procedure Methods 0.000 description 5
- 239000011573 trace mineral Substances 0.000 description 5
- LFQSCWFLJHTTHZ-UHFFFAOYSA-N Ethanol Chemical compound CCO LFQSCWFLJHTTHZ-UHFFFAOYSA-N 0.000 description 4
- 238000005273 aeration Methods 0.000 description 4
- 230000001476 alcoholic effect Effects 0.000 description 4
- 239000012267 brine Substances 0.000 description 4
- 238000004821 distillation Methods 0.000 description 4
- 239000004615 ingredient Substances 0.000 description 4
- 150000002632 lipids Chemical class 0.000 description 4
- 235000021574 pickled cabbage Nutrition 0.000 description 4
- 235000021110 pickles Nutrition 0.000 description 4
- 238000011160 research Methods 0.000 description 4
- HPALAKNZSZLMCH-UHFFFAOYSA-M sodium;chloride;hydrate Chemical compound O.[Na+].[Cl-] HPALAKNZSZLMCH-UHFFFAOYSA-M 0.000 description 4
- 235000013619 trace mineral Nutrition 0.000 description 4
- 241001550224 Apha Species 0.000 description 3
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- 244000088415 Raphanus sativus Species 0.000 description 3
- 235000006140 Raphanus sativus var sativus Nutrition 0.000 description 3
- HCHKCACWOHOZIP-UHFFFAOYSA-N Zinc Chemical compound [Zn] HCHKCACWOHOZIP-UHFFFAOYSA-N 0.000 description 3
- 150000003863 ammonium salts Chemical class 0.000 description 3
- 235000014633 carbohydrates Nutrition 0.000 description 3
- 150000001720 carbohydrates Chemical class 0.000 description 3
- 230000010261 cell growth Effects 0.000 description 3
- 238000011534 incubation Methods 0.000 description 3
- 230000000813 microbial effect Effects 0.000 description 3
- 239000010452 phosphate Substances 0.000 description 3
- NBIIXXVUZAFLBC-UHFFFAOYSA-K phosphate Chemical compound [O-]P([O-])([O-])=O NBIIXXVUZAFLBC-UHFFFAOYSA-K 0.000 description 3
- 230000005180 public health Effects 0.000 description 3
- 239000011701 zinc Substances 0.000 description 3
- 229910052725 zinc Inorganic materials 0.000 description 3
- XEEYBQQBJWHFJM-UHFFFAOYSA-N Iron Chemical compound [Fe] XEEYBQQBJWHFJM-UHFFFAOYSA-N 0.000 description 2
- 229910052925 anhydrite Inorganic materials 0.000 description 2
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 description 2
- OSGAYBCDTDRGGQ-UHFFFAOYSA-L calcium sulfate Chemical compound [Ca+2].[O-]S([O-])(=O)=O OSGAYBCDTDRGGQ-UHFFFAOYSA-L 0.000 description 2
- 230000008859 change Effects 0.000 description 2
- 238000012512 characterization method Methods 0.000 description 2
- 238000011109 contamination Methods 0.000 description 2
- 238000001816 cooling Methods 0.000 description 2
- 239000012153 distilled water Substances 0.000 description 2
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- 229910000359 iron(II) sulfate Inorganic materials 0.000 description 2
- 238000002955 isolation Methods 0.000 description 2
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- 239000000203 mixture Substances 0.000 description 2
- 239000010813 municipal solid waste Substances 0.000 description 2
- 235000015097 nutrients Nutrition 0.000 description 2
- 229910052760 oxygen Inorganic materials 0.000 description 2
- 239000001301 oxygen Substances 0.000 description 2
- 235000021108 sauerkraut Nutrition 0.000 description 2
- 238000000926 separation method Methods 0.000 description 2
- 239000000243 solution Substances 0.000 description 2
- 241000894007 species Species 0.000 description 2
- 238000009966 trimming Methods 0.000 description 2
- LWIHDJKSTIGBAC-UHFFFAOYSA-K tripotassium phosphate Chemical compound [K+].[K+].[K+].[O-]P([O-])([O-])=O LWIHDJKSTIGBAC-UHFFFAOYSA-K 0.000 description 2
- 238000009423 ventilation Methods 0.000 description 2
- 210000005253 yeast cell Anatomy 0.000 description 2
- NWONKYPBYAMBJT-UHFFFAOYSA-L zinc sulfate Chemical compound [Zn+2].[O-]S([O-])(=O)=O NWONKYPBYAMBJT-UHFFFAOYSA-L 0.000 description 2
- 241000228212 Aspergillus Species 0.000 description 1
- 241001225321 Aspergillus fumigatus Species 0.000 description 1
- 241000228245 Aspergillus niger Species 0.000 description 1
- OYPRJOBELJOOCE-UHFFFAOYSA-N Calcium Chemical compound [Ca] OYPRJOBELJOOCE-UHFFFAOYSA-N 0.000 description 1
- 241000192418 Candida halonitratophila Species 0.000 description 1
- 241000222128 Candida maltosa Species 0.000 description 1
- 241001123652 Candida versatilis Species 0.000 description 1
- 240000004160 Capsicum annuum Species 0.000 description 1
- 235000008534 Capsicum annuum var annuum Nutrition 0.000 description 1
- 235000007862 Capsicum baccatum Nutrition 0.000 description 1
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 description 1
- 239000004215 Carbon black (E152) Substances 0.000 description 1
- RYGMFSIKBFXOCR-UHFFFAOYSA-N Copper Chemical compound [Cu] RYGMFSIKBFXOCR-UHFFFAOYSA-N 0.000 description 1
- 241000235646 Cyberlindnera jadinii Species 0.000 description 1
- 108090000790 Enzymes Proteins 0.000 description 1
- 102000004190 Enzymes Human genes 0.000 description 1
- 240000005979 Hordeum vulgare Species 0.000 description 1
- 235000007340 Hordeum vulgare Nutrition 0.000 description 1
- 238000007696 Kjeldahl method Methods 0.000 description 1
- FYYHWMGAXLPEAU-UHFFFAOYSA-N Magnesium Chemical compound [Mg] FYYHWMGAXLPEAU-UHFFFAOYSA-N 0.000 description 1
- PWHULOQIROXLJO-UHFFFAOYSA-N Manganese Chemical compound [Mn] PWHULOQIROXLJO-UHFFFAOYSA-N 0.000 description 1
- 244000294411 Mirabilis expansa Species 0.000 description 1
- 235000015429 Mirabilis expansa Nutrition 0.000 description 1
- 240000007594 Oryza sativa Species 0.000 description 1
- 235000007164 Oryza sativa Nutrition 0.000 description 1
- ISWSIDIOOBJBQZ-UHFFFAOYSA-N Phenol Chemical compound OC1=CC=CC=C1 ISWSIDIOOBJBQZ-UHFFFAOYSA-N 0.000 description 1
- 241000444900 Pseudocercospora mori Species 0.000 description 1
- 241001633102 Rhizobiaceae Species 0.000 description 1
- 241000698291 Rugosa Species 0.000 description 1
- 244000253911 Saccharomyces fragilis Species 0.000 description 1
- 235000018368 Saccharomyces fragilis Nutrition 0.000 description 1
- 241000235033 Zygosaccharomyces rouxii Species 0.000 description 1
- 238000002835 absorbance Methods 0.000 description 1
- 239000002253 acid Substances 0.000 description 1
- BFNBIHQBYMNNAN-UHFFFAOYSA-N ammonium sulfate Chemical compound N.N.OS(O)(=O)=O BFNBIHQBYMNNAN-UHFFFAOYSA-N 0.000 description 1
- 229910052921 ammonium sulfate Inorganic materials 0.000 description 1
- 235000011130 ammonium sulphate Nutrition 0.000 description 1
- 229940091771 aspergillus fumigatus Drugs 0.000 description 1
- 230000001580 bacterial effect Effects 0.000 description 1
- 235000013405 beer Nutrition 0.000 description 1
- 108010051210 beta-Fructofuranosidase Proteins 0.000 description 1
- 239000006227 byproduct Substances 0.000 description 1
- 239000011575 calcium Substances 0.000 description 1
- 229910052791 calcium Inorganic materials 0.000 description 1
- 238000009924 canning Methods 0.000 description 1
- 239000001728 capsicum frutescens Substances 0.000 description 1
- 229910052799 carbon Inorganic materials 0.000 description 1
- 238000005119 centrifugation Methods 0.000 description 1
- 238000007796 conventional method Methods 0.000 description 1
- 229910052802 copper Inorganic materials 0.000 description 1
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- 235000019784 crude fat Nutrition 0.000 description 1
- 238000012136 culture method Methods 0.000 description 1
- 230000003247 decreasing effect Effects 0.000 description 1
- 235000013399 edible fruits Nutrition 0.000 description 1
- 238000005516 engineering process Methods 0.000 description 1
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- 229930195733 hydrocarbon Natural products 0.000 description 1
- 150000002430 hydrocarbons Chemical class 0.000 description 1
- 230000005764 inhibitory process Effects 0.000 description 1
- 238000011081 inoculation Methods 0.000 description 1
- 239000002054 inoculum Substances 0.000 description 1
- 239000001573 invertase Substances 0.000 description 1
- 235000011073 invertase Nutrition 0.000 description 1
- 229910052742 iron Inorganic materials 0.000 description 1
- BAUYGSIQEAFULO-UHFFFAOYSA-L iron(2+) sulfate (anhydrous) Chemical compound [Fe+2].[O-]S([O-])(=O)=O BAUYGSIQEAFULO-UHFFFAOYSA-L 0.000 description 1
- 239000011777 magnesium Substances 0.000 description 1
- 229910052749 magnesium Inorganic materials 0.000 description 1
- 229910052748 manganese Inorganic materials 0.000 description 1
- 239000011572 manganese Substances 0.000 description 1
- 239000000463 material Substances 0.000 description 1
- 239000011785 micronutrient Substances 0.000 description 1
- 235000013369 micronutrients Nutrition 0.000 description 1
- 235000013536 miso Nutrition 0.000 description 1
- 235000021049 nutrient content Nutrition 0.000 description 1
- 239000010815 organic waste Substances 0.000 description 1
- 230000008520 organization Effects 0.000 description 1
- 238000010979 pH adjustment Methods 0.000 description 1
- 230000007918 pathogenicity Effects 0.000 description 1
- OQUKIQWCVTZJAF-UHFFFAOYSA-N phenol;sulfuric acid Chemical compound OS(O)(=O)=O.OC1=CC=CC=C1 OQUKIQWCVTZJAF-UHFFFAOYSA-N 0.000 description 1
- 229910000160 potassium phosphate Inorganic materials 0.000 description 1
- 235000011009 potassium phosphates Nutrition 0.000 description 1
- 238000004321 preservation Methods 0.000 description 1
- 239000002994 raw material Substances 0.000 description 1
- 238000004064 recycling Methods 0.000 description 1
- 238000012552 review Methods 0.000 description 1
- 235000009566 rice Nutrition 0.000 description 1
- 235000014102 seafood Nutrition 0.000 description 1
- 235000013555 soy sauce Nutrition 0.000 description 1
- 238000003756 stirring Methods 0.000 description 1
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- 239000000758 substrate Substances 0.000 description 1
- 150000008163 sugars Chemical class 0.000 description 1
- 238000012360 testing method Methods 0.000 description 1
- 230000001988 toxicity Effects 0.000 description 1
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Classifications
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- 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
- C12N1/14—Fungi; Culture media therefor
- C12N1/16—Yeasts; Culture media therefor
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B09—DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
- B09B—DISPOSAL OF SOLID WASTE NOT OTHERWISE PROVIDED FOR
- B09B3/00—Destroying solid waste or transforming solid waste into something useful or harmless
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- Chemical & Material Sciences (AREA)
- Engineering & Computer Science (AREA)
- Health & Medical Sciences (AREA)
- Bioinformatics & Cheminformatics (AREA)
- Genetics & Genomics (AREA)
- Biotechnology (AREA)
- Organic Chemistry (AREA)
- Zoology (AREA)
- Wood Science & Technology (AREA)
- Mycology (AREA)
- Microbiology (AREA)
- Biomedical Technology (AREA)
- Botany (AREA)
- Virology (AREA)
- Tropical Medicine & Parasitology (AREA)
- Biochemistry (AREA)
- General Engineering & Computer Science (AREA)
- General Health & Medical Sciences (AREA)
- Medicinal Chemistry (AREA)
- Micro-Organisms Or Cultivation Processes Thereof (AREA)
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Abstract
Description
본 발명은 염이 과량 함유된 배지, 특히 김치 제조시 발생하는 배추 절임폐수에서 성장할 수 있는 효모 피키아 귈리어몬디, 특히 신규 효모 균주 피키아 귈리어몬디 A9(Pichia guilliermondii A9)를 배양하여 단세포 단백질로 사용할 수 있는 균체를 생산하는 방법, 상기 균주를 이용하여 배추 절임폐수 등의 폐기물을 처리하는 방법, 및 피키아 귈리어몬디 A9에 관한 것이다.The present invention is a single-cell protein by culturing yeast Pichia cullimondi, especially the novel yeast strain Pichia guilliermondii A9, which can be grown in a salt-containing medium, especially in the cabbage pickling wastewater generated during kimchi production. The present invention relates to a method for producing microbial cells that can be used as a method for treating wastes such as Chinese cabbage pickled wastewater using the strain, and Pichia ceriamondi A9.
김치는 우리나라의 대표적 전통 발효식품으로서 1980년대부터 본격적인 산업화가 시작되었으며 공장에서 생산되는 김치는 연간 약 14만 톤으로 조사되었으나, 수출과 내수의 증가로 해마다 약 15∼20%의 증가 추세에 있다(Choi, T. D., An Analysis on the Market Organization of Kimchi Industry, Doctoral Thesis, Seoul National University, Seoul, 1994). 이와 같은 김치의 산업화에 따라 최근 김치의 과학적인 생산, 가공, 보존을 위한 연구가 활발히 이루어지고 있으나, 아직까지 김치제조 중 절임 과정에서 부산물로 발생하는 절임폐수에 관한 연구는 전무한 실정이다.Kimchi is Korea's representative traditional fermented food, and industrialization started in earnest from the 1980s. Kimchi produced at the factory was surveyed at 140,000 tons per year, but it is increasing by 15 ~ 20% every year due to the increase in exports and domestic demand. Choi, TD, An Analysis on the Market Organization of Kimchi Industry, Doctoral Thesis, Seoul National University, Seoul, 1994). As a result of the industrialization of kimchi, researches for scientific production, processing, and preservation of kimchi have been actively conducted. However, there is no research on pickling wastewater generated as a by-product during pickling during kimchi production.
김치공장의 절임폐수는 그 발생량 및 성분이 조사, 보고된 바 없으나 현재 연간 약 8∼10만 톤 정도가 발생하는 것으로 추정된다. 절임폐수는 배추의 절임 과정 중 배추로부터 유출된 당 성분 등이 함유되어 있어서 BOD 및 COD가 높고, 소금의 함량이 약 7∼10% 정도로 매우 높아서 현재와 같이 이를 그대로 버리는 것은 수질 및 토양오염을 일으키는 심각한 문제가 되고 있으며, 또한 절임폐수의 유기 성분을 균체 생산 및 유용물질 생산을 위한 기질로 재활용할 가치가 있는 폐수로 볼 수 있다.The amount and composition of pickled wastewater at the Kimchi plant has not been investigated and reported, but it is estimated to generate about 80,000 to 100,000 tons per year. Pickled wastewater contains sugar, which is extracted from cabbage during pickling, and has a high BOD and COD, and a very high salt content of about 7-10%. It is a serious problem and can also be seen as a wastewater that is worth recycling the organic components of pickled wastewater as a substrate for cell production and useful material production.
지금까지 식품공장의 폐수를 이용한 균체 생산에 관한 연구로는 국내에서는 주로 알콜 발효공장의 증류 폐액을 이용하여 효모를 생산하고 동시에 폐수 처리 효과를 얻기 위한 연구 결과가 보고되었다. 이 등(Lee, H. Y. et al., Kor. J. Appl. Microbiol. Bioeng., 10, 95∼100(1982))은 절간 고구마 원료의 주정 폐액에서 효모 토룰롭시스 칸디다(Torulopsis candida)를 배양하여 BOD를 39% 감소시켰다고 보고하였으며, 김 등(Kim, et al., Kor. J. Appl. Microbiol. Biotechnol., 21, 281∼287(1993))은 쌀보리 알콜 발효 증류 폐액에서 칸디다 루고사(Candida rugosa)를 배양한 결과 균체 생산량은 높았으나 COD 감소 효과는 낮은 편이었다고 보고하였다. 또한, 이 등(Lee, C. Y. et al., Korean J. Biotechnol. Boeng., 8, 172∼177(1993))은 단세포 지질 생산에 적합한 효모로 로도토룰라 글루티니스(Rhodotolula glutinis)를 알콜 발효 증류 폐액에서 배양하여 4g/ℓ의 단세포 지질과 88.7%의 BOD 감소 효과를 얻었다고 보고하였다. 한편, 조 등(Cho, S. H. et al., J. of Korean Agric. Chem. Soc., 32, 424∼434(1989))은 식품공장 폐수의 특성을 조사하고 그 중 주정공장 폐수에서 미생물을 배양한 결과 90% 이상의 BOD와 COD 감소 효과를 얻었다고 보고하였다.Until now, as a study on the production of cells using wastewater in food factories, studies have been reported in Korea to produce yeast using distillation wastewater from alcohol fermentation plants and at the same time obtain the wastewater treatment effect. Lee et al. (Lee, HY et al., Kor. J. Appl. Microbiol. Bioeng., 10, 95-100 (1982)), were used to culture yeast Torulopsis candida in alcoholic liquor wastewater from intercalated sweet potatoes. BOD reported a 39% reduction, and Kim et al. (Kim, et al., Kor. J. Appl. Microbiol. Biotechnol., 21, 281-287 (1993)) reported Candida lugosa in rice barley alcohol fermentation distillation wastewater. rugosa) showed higher cell production but lower COD reduction. Lee et al. (Lee, CY et al., Korean J. Biotechnol. Boeng., 8, 172 to 177 (1993)) also disclose alcohol fermentation distillation of Rhodotolula glutinis as a yeast suitable for single cell lipid production. It was reported that culturing in the waste solution resulted in 4 g / L single cell lipids and 88.7% BOD reduction. On the other hand, Cho et al. (Cho, SH et al., J. of Korean Agric. Chem. Soc., 32, 424-434 (1989)) investigated the characteristics of food plant wastewater and cultivated the microorganisms in alcohol factory wastewater. As a result, more than 90% reported BOD and COD reduction effect.
외국에서는 행 등(Hang, Y. D. et al., J. of Milk and Food Technol., 35, 432∼435(1972))이 김치와 유사한 채소 발효 식품인 사우어크라우트(sauerkraut) 생산시 발생하는 폐수가 BOD가 매우 높고, pH가 낮으며, NaCl 농도가 약 3 - 4% (w/v)로 높으므로 상법에 의한 폐수 처리가 부적합하다고 하였으며, 이 폐수에 칸디다 유틸리스(Candida utilis)와 아스퍼질러스 나이거(Aspergillus niger)를 배양함으로써 BOD를 감소시키고 균체를 생산하는 방법을 보고하였다(Hang, Y. D., et al., Progress in Water Technol., 8, 381∼384(1976)). 또한 사우어크라우트 폐수에서 칸디다 유틸리스를 배양하여 BOD를 90% 이상 감소시키는 동시에 식용 또는 사료로 쓰이거나, 인버테이즈(invertase)의 효소원으로 사용할 수 있는 균체를 생산할 수 있다고 보고하였다(Hang, Y. D., Process Biochem., 12, 27∼28(1977)). 한편, 웰쉬와 잘(Welsh, F. W. and R. R. Zall, Process Biochem., 19, 122∼123(1984))은 수산물 절임 폐수에 칸디다 유틸리스를 배양하여 균체를 생산하는 방법을 보고하였다. 일본국 특허 공개 제 평4-173089 호에는 염농도 0.2-7% (w/w)의 범위에서 페놀을 분해할 수 있는 리조비엄 과(Rhizobiaceae)에 속하는 세균이 개시되어 있다.In foreign countries, BOD (Hang, YD et al., J. of Milk and Food Technol., 35, 432-435 (1972)) produces wastewater from the production of sauerkraut, a vegetable fermented food similar to kimchi. Is very high, pH is low, NaCl concentration is about 3-4% (w / v), and wastewater treatment by conventional methods is inadequate. Candida utilis and Aspergillus na A method of reducing BOD and producing cells was reported by culturing Aspergillus niger (Hang, YD, et al., Progress in Water Technol., 8, 381-384 (1976)). It has also been reported that cultivating Candida utilities in Sourkraut wastewater can reduce the BOD by more than 90% and produce cells that can be used for food or feed or as an enzyme source of invertase (Hang, YD). , Process Biochem., 12, 27-28 (1977). On the other hand, Welsh and Fal (Welsh, F. W. and R. R. Zall, Process Biochem., 19, 122-123 (1984)) reported a method for producing cells by culturing Candida utility in pickled aquatic wastewater. Japanese Patent Laid-Open No. 4-173089 discloses a bacterium belonging to the Rhizobiaceae family capable of decomposing phenol in the salt concentration range of 0.2-7% (w / w).
그러나, 지금까지 염농도가 더욱 높은 김치공장에서 발생하는 절임폐수에 관하여는 조사된 바 없으며, 이 폐수를 이용한 균체 생산에 대한 연구는 전혀 없는 실정이다.However, no pickling wastewater from the Kimchi plant with higher salt concentration has been investigated until now, and there is no research on cell production using the wastewater.
따라서, 본 발명의 목적은 고농도의 염이 함유된 환경에서 성장할 수 있고 단세포 단백질로 이용될 수 있는 신규 균주를 제공하는 것이다.Accordingly, it is an object of the present invention to provide novel strains that can grow in an environment containing high concentrations of salt and can be used as single cell proteins.
본 발명의 다른 목적은 염이 함유된 배지에서 피키아 귈리어몬디를 배양하여 단세포 단백질로 사용할 수 있는 균체를 생산하는 방법을 제공하는 것이다.Another object of the present invention is to provide a method for producing cells that can be used as a single-cell protein by culturing Pichia cerimondi in a salt-containing medium.
본 발명의 다른 목적은 피키아 귈리어몬디를 이용하여 고농도의 염이 함유된 폐기물을 처리하는 방법을 제공하는 것이다.It is another object of the present invention to provide a method for treating waste containing high concentrations of salts using Pichia ceralimondi.
도 1a 내지 1c는 배추 절임 폐수에서 배양할 때 피키아 귈리어몬디(Pichia guilliermondii) A9의 성장에 대한 온도, pH 및 NaCl 농도의 영향을 각각 나타낸 것이다.Figures 1a to 1c show the effect of temperature, pH and NaCl concentration on the growth of Pichia guilliermondii A9 when incubated in pickled cabbage wastewater, respectively.
도 2는 배추 절임 폐수(pH 4.0, 8% NaCl)에서 30℃로 배양할 때 피키아 귈리어몬디 A9의 성장에 대한 통기량의 영향을 나타낸 것이다.Figure 2 shows the effect of aeration on the growth of Pichia ceriamondi A9 when incubated at 30 ℃ in pickled waste water (pH 4.0, 8% NaCl).
도 3a 및 3b는 배추 절임 폐수(pH 4.0, 8% NaCl)에서 30℃로 배양할 때 피키아 귈리어몬디 A9의 성장에 대한 황산 암모늄 및 인산 칼륨의 영향을 각각 나타낸 것이다.3A and 3B show the effects of ammonium sulfate and potassium phosphate on the growth of Pichia cerimondi A9 when incubated at 30 ° C. in Chinese cabbage pickled wastewater (pH 4.0, 8% NaCl).
도 4는 배추 절임 폐수(pH 4.0, 8% NaCl)에서 30℃로 배양할 때 피키아 귈리어몬디 A9의 성장에 대한 미량 영양성분의 영향을 나타낸 것이다.Figure 4 shows the effect of micronutrients on the growth of Pichia ceriamondi A9 when incubated at 30 ℃ in pickled waste water (pH 4.0, 8% NaCl).
도 5는 배추 절임 폐수(pH 4.0, 8% NaCl)에서 30℃로 배양할 때 피키아 귈리어몬디 A9의 성장에 대한 황산 아연 농도의 영향을 나타낸 것이다.FIG. 5 shows the effect of zinc sulfate concentration on the growth of Pichia ceriamondi A9 when incubated at 30 ° C. in Chinese cabbage pickled wastewater (pH 4.0, 8% NaCl).
도 6은 30℃에서 피키아 귈리어몬디 A9의 성장도중 배추 절임 폐수의 BOD 감소를 나타낸 것이다.Figure 6 shows the BOD reduction of the Chinese cabbage pickling wastewater during the growth of Pichia ceriamondi A9 at 30 ℃.
도 7은 피키아 귈리어몬디 A9과 기타 내염성 효모의 배추 절임 폐수에서의 생육을 나타낸 것이다.Figure 7 shows the growth in pickled wastewater of Chinese cabbage pickles of Pichia ceriamondi A9 and other saline tolerant yeast.
상기 목적에 따라, 본 발명에서는 배추 절임폐수와 같이 고농도의 염이 함유된 환경에서 성장할 수 있는 신규 효모 균주 피키아 귈리어몬디(Pichia guilliermondii) A9이 제공된다.In accordance with the above object, the present invention provides a novel yeast strain Pichia guilliermondii A9 capable of growing in an environment containing a high concentration of salt such as Chinese cabbage pickled waste water.
피. 귈리어몬디 A9는 온도 약 20℃ 내지 42℃, pH 약 2 내지 11에서 우수한 생육을 나타내며, 특히 NaCl 농도 약 18%에서도 생육이 가능하다. 특히, 이 균주는 배추 절임 폐수와 같이 고농도(7-12%)의 NaCl을 함유하는 각종 배지에서 생육이 가능하며, 배추 절임 폐수 등에 함유된 유기물 이용 능력이 우수하여 상기 균주를 배추 절임 폐수 등에서 배양함으로써 단세포 단백질을 효과적으로 생산하면서 동시에 유기물을 제거할 수 있다. 상기 균주는 배추 절임 폐수 등에서의 생육 pH, 생육 온도 및 생육 염농도 범위가 넓은 균주이므로 상이한 절임 공정에 따라 성분에 차이가 있는 임의의 절임폐수에서도 특별한 부가적 처리없이 성장할 수 있다. 더구나, 본 발명의 균주는 배추 절임폐수에서 배양할 때 공지의 피. 귈리어몬디 균주보다 높은 생육을 나타내고, 특히 40℃의 고온에서 공지의 피. 귈리어몬디 균주보다 훨씬 우수한 생육을 나타내므로 일반적으로 공업적인 미생물 배양시 발생하는 발효열에 의한 온도 상승에 대한 냉각비용을 절감할 수 있다는 측면에서 공업적으로 매우 유리하다.blood. Cullimondi A9 shows excellent growth at a temperature of about 20 ° C. to 42 ° C., and a pH of about 2 to 11, particularly at about 18% NaCl. In particular, the strain can be grown in a variety of medium containing high concentrations (7-12%) of NaCl, such as Chinese cabbage pickled waste water, and the strain is excellent in the use of organic matter contained in the Chinese cabbage pickled waste water, such that the strain is cultured in pickled cabbage waste water, etc. This allows for efficient production of single cell proteins and at the same time removing organics. Since the strain has a wide range of growth pH, growth temperature and growth salt concentration in the Chinese cabbage pickling wastewater, etc., it can grow without any additional treatment in any pickling wastewater having different ingredients according to different pickling processes. Moreover, the strains of the present invention are known blood when cultured in Chinese cabbage pickled wastewater. It shows higher growth than vilimondi strain, especially known blood at high temperature of 40 ° C. It is much industrially advantageous in terms of reducing the cooling cost against temperature rise due to fermentation heat generated during industrial microbial growth because it shows much better growth than vilimondi strains.
본 발명에서는 또한 피. 귈리어몬디 A9를 포함하는 피. 귈리어몬디 종(genus)들을 고농도의 염을 포함하는 배지에서 배양하여 단세포 단백질로 사용할 수 있는 균체를 생산할 수 있음을 발견하였다. 구체적으로는, 피. 귈리어몬디를 초기 pH가 2 내지 11, NaCl 농도가 0.5 내지 18%인 배지에 접종하고, 20℃ 내지 42℃의 온도에서 진탕배양한 후, 배양액으로부터 원심분리 등의 방법에 의해 균체를 회수하고 세척 및 건조하여 건조 균체를 얻음으로써 단세포 단백질을 얻을 수 있다. 피. 귈리어몬디를 pH 4, NaCl 농도 12% 이하인 배지에서 30℃로 진탕 배양하는 것이 가장 바람직하며, 배양 초기 pH를 3∼4 정도로 낮게 조절하여 배양하면 세균에 의한 오염을 피할 수 있어 유리하다. 통기량은 생육에 크게 영향을 미치지 않으며 0.5 vvm 정도면 충분하다.In the present invention also p. Blood containing Cerealmondy A9. It has been found that the C. mori species can be cultured in a medium containing a high concentration of salt to produce cells that can be used as single cell proteins. Specifically, blood. After inoculating Villimondi into a medium having an initial pH of 2 to 11 and a NaCl concentration of 0.5 to 18%, shaking culture at a temperature of 20 ° C to 42 ° C, cells were recovered from the culture by a method such as centrifugation. Single cell proteins can be obtained by washing and drying to obtain dry cells. blood. It is most preferable to cultivate the cultivar shaker at 30 ° C. in a medium having a pH of 4 and NaCl of 12% or less, and culturing by adjusting the initial pH of the culture to a low level of about 3 to 4 is advantageous because it can avoid contamination by bacteria. Aeration does not significantly affect growth, and 0.5 vvm is sufficient.
상기의 방법에 의해 배양한 균체는 일반적인 단세포 단백질 생산 공정(Solomons, G. L., CRC Cirtical Reviews in Biotechnology, 1(1), 21∼58 (1982))과 같이 균체의 회수, 건조, 분쇄의 과정을 거쳐 제품화할 수 있다.The cells cultured by the above method were recovered, dried and pulverized as in the general unicellular protein production process (Solomons, GL, CRC Cirtical Reviews in Biotechnology, 1 (1), 21-58 (1982)). It can be commercialized.
본 발명의 방법에 따라 생산된 균체는 약 40%의 높은 조단백질 함량을 나타내므로 단세포 단백질로서 유용하게 이용될 수 있다. 피키아 귈리어몬디는 요시다 및 하시모토(Yoshida, A. and Hashimoto, K., Agric. Biol. Chem., 50, 2117-2120 (1986a))와 마우어스베르거 등(Mauersberger et al., (1996) Candida maltosa, pp. 411-480, In Nonconventional Yeasts in Biotechnology, Wolf, K. ed. Springer-Verlag, Berlin, Germany)에 의해 보고된 바와 같이 병원성이 없거나 병원성을 나타낼 가능성이 거의 없다. 또한, 균체의 건조과정 등에 의한 열처리를 통해 사균화시킨 균체를 단세포 단백질로 사용할 경우 독성에 대한 위험도는 더욱 줄일 수 있다.The cells produced according to the method of the present invention exhibit a high crude protein content of about 40% and can be usefully used as single cell proteins. Pichia ceriamondi includes Yoshida, A. and Hashimoto, K., Agric. Biol. Chem., 50, 2117-2120 (1986a) and Mauersberger et al. (1996). As reported by Candida maltosa, pp. 411-480, In Nonconventional Yeasts in Biotechnology, Wolf, K. ed.Springer-Verlag, Berlin, Germany), there is little or no pathogenicity. In addition, the risk of toxicity can be further reduced if the cells that have been sterilized through heat treatment by the drying process of the cells are used as single cell proteins.
본 발명에서 피. 귈리어몬디를 배양하기 위한 배지로서는 고농도의 염을 포함하는 임의의 배지를 사용할 수 있고, 특히 김치 제조 공장의 절임 폐수 및 폐기물, 절임채소 가공공장(피클류, 단무지 생산 공장 등)의 절임 폐수 및 폐기물, 장류 가공 폐수 및 폐기물, 수산물 염장 가공 폐수 및 폐기물, 염장 육가공(햄 등) 폐수 및 폐기물 등 고농도의 염을 포함하는 폐기물들을 사용할 수 있다.Blood in the present invention. Any medium containing a high concentration of salt can be used as a medium for culturing vili mondi, and in particular, pickled wastewater and wastes from a kimchi manufacturing plant, pickled wastewater from pickled vegetable processing plants (pickles, pickled radish production plants, etc.) and Wastes containing high concentrations of salts can be used, such as waste, enteric processed wastewater and waste, aquatic salted processed wastewater and waste, salted meat processing (ham, etc.) wastewater and waste.
필요에 따라, 상기 배지에 임의의 영양 성분을 첨가하여 균체의 생육을 증진시킬 수 있으며, 미량원소로서 약 0.5 mM의 아연을 첨가하면 균체의 생육이 증진된다. 그러나, 0.5 mM의 아연의 첨가에 의한 균체 증가 효과는 크지 않으므로 첨가하지 않아도 무방하다.If necessary, any nutrient can be added to the medium to enhance the growth of the cells, and the addition of about 0.5 mM of zinc as a trace element enhances the growth of the cells. However, the effect of cell growth by the addition of 0.5 mM zinc is not so large, and may not be added.
또한, 본 발명에서는 미생물을 이용하여 폐기물을 처리하는 방법에 있어서, 염이 함유된 폐기물에 균주로서 내염성인 피. 귈리어몬디를 접종하고, 상기 균주를 배양하여 유기물을 분해하는 것을 특징으로 하는 폐기물 처리방법이 제공된다. 균주의 배양 방법은 상기에서 균체 생산 방법과 관련하여 설명한 것과 동일하고, 본 발명의 방법으로 처리할 수 있는 폐기물들은 피. 귈리어몬디의 균체 생산과 관련하여 상기에서 예시한 고농도의 염을 함유하는 폐수 및 폐기물들을 포함한다.In addition, in the present invention, a method for treating waste by using microorganisms, blood, which is salt-tolerant as a strain in the waste containing salt. There is provided a waste treatment method comprising inoculating Valimonty and culturing the strain to decompose organic matter. The culture method of the strain is the same as described above with respect to the cell production method, wastes that can be treated by the method of the present invention. Wastewater and wastes containing high concentrations of salts exemplified above in connection with cell production of Zurimondi.
특히, 김치 제조 공장에서 배출되는 김치 절임폐수를 처리할 때, 김치 절임 폐수에 배추 쓰레기 착즙액을 첨가하는 공정을 도입하면 김치 제조 공장에서 배출되는 두 가지 폐기물인 배추 절임폐수와 배추 쓰레기를 동시에 처리하는 효과가 있다.In particular, when the kimchi pickled wastewater discharged from the kimchi manufacturing plant is introduced, the process of adding the cabbage trash juice to the kimchi pickled wastewater simultaneously treats the two wastes that are discharged from the kimchi manufacturing plant: Chinese cabbage pickled waste and Chinese cabbage waste. It is effective.
본 발명의 균주를 이용하여 배추 절임폐수를 처리하는 경우 24시간 이내에 BOD를 약 90% 이상 감소시키므로 본 발명의 폐수처리 방법은 매우 간단하면서도 유기물 제거 효과가 뛰어나다. 배추 절임 폐수에 배추 쓰레기 착즙액을 첨가하여 배양한 경우에도 유기물 제거 효과가 우수하여 20% 이내로 첨가한 경우는 24시간 이내에, 30% 첨가시에는 48시간 이내에 환원당 함량이 완전히 소모된다.When the cabbage pickled wastewater is treated using the strain of the present invention, since the BOD is reduced by about 90% or more within 24 hours, the wastewater treatment method of the present invention is very simple and excellent in removing organic matters. Even when the cabbage waste juice was added to the cabbage pickling waste water, the reduced organic sugar content was completely consumed within 24 hours when added within 20% and within 48 hours when added within 20%.
이하 본 발명을 다음과 같은 실시예에 의하여 더욱 상세하게 설명하고자 한다. 단, 다음의 실시예는 본 발명을 예시하기 위한 것일 뿐, 본 발명의 범위가 이것들 만으로 한정되는 것은 아니다. 본 실시예에서는 김치 제조 공장의 절임 폐수 및 폐기물, 절임채소 가공공장(피클류, 단무지 생산 공장 등)의 절임 폐수 및 폐기물, 장류 가공 폐수 및 폐기물, 수산물 염장 가공 폐수 및 폐기물, 염장 육가공(햄 등) 폐수 및 폐기물 중에서 배추 절임폐수를 이용하였다.Hereinafter, the present invention will be described in more detail with reference to the following examples. However, the following Examples are only for illustrating the present invention, and the scope of the present invention is not limited to these. In this embodiment, the pickled wastewater and waste in the kimchi manufacturing plant, pickled wastewater and waste from pickled vegetable processing plants (pickles, pickled radish production plants, etc.), enteric processed wastewater and waste, aquatic salted processed wastewater and waste, salted meat processing (ham, etc.) ) Chinese cabbage pickled wastewater was used.
실시예 1: 배추 절임폐수의 특성 분석Example 1 Characterization of Chinese Cabbage Pickling Wastewater
(1) 절임폐수(1) Pickled wastewater
경기도 소재의 생산 규모가 다른 4개의 김치공장으로부터 배추 절임폐수 시료를 수집하였다.Chinese cabbage pickled wastewater samples were collected from four kimchi factories with different production scales in Gyeonggi-do.
또한 균일한 성분의 절임폐수를 얻기 위하여 김치공장에서 배추를 절이는 공정과 유사한 과정에 따라 다음과 같이 실험실에서 절임폐수를 제조하였다. 즉, 시장에서 구입한 배추를 다듬어 4조각으로 자른 후 10% 소금물에서 15℃를 유지하면서 15시간 동안 절였다. 이때 배추 무게와 소금물의 비율은 약 2:3 (w:v)으로 하였으며, 절인물은 여과지(Whatman No. 2)를 사용하여 걸렀다. 또한, 김치공장에서 1회 절임에 사용한 소금물을 2회 또는 3회 재사용하는 것을 감안하여 1회 절인 배추중 일부를 동일한 조건에서 2회 절였으며, 이때 1회 사용한 절임폐수와 재 사용한 절임폐수의 성분차이도 비교하였다.In addition, in order to obtain a pickled wastewater with a uniform composition, the pickled wastewater was prepared in the laboratory as follows, similar to the process of pickling cabbage at the Kimchi factory. In other words, the cabbage purchased in the market was cut into 4 pieces and then marinated for 15 hours while maintaining 15 ° C in 10% brine. At this time, the cabbage weight and brine ratio were about 2: 3 (w: v), and the pickled water was filtered using filter paper (Whatman No. 2). In addition, in consideration of the reuse of the brine used for pickling once or twice in the Kimchi plant, some of the pickled cabbages were pickled twice under the same conditions.In this case, the ingredients of pickled wastewater and reused pickled wastewater The differences were also compared.
절임폐수에서 효모의 생육 특성을 조사할 경우는 실험실 제조 절임폐수를 사용하였으며, 절임폐수는 NaCl을 사용하여 NaCl농도가 8%가 되도록 하였고, 환원당 농도는 약 1.0 g/ℓ가 되도록 글루코즈를 첨가하여 표준화하여 사용하였다.In order to investigate the growth characteristics of yeast in pickled wastewater, laboratory-made pickled wastewater was used. The pickled wastewater was made with NaCl so that the NaCl concentration was 8%, and the reducing sugar concentration was about 1.0 g / l. Standardized.
(2) 절임폐수의 특성 분석(2) Characterization of Pickled Wastewater
(1)에서 준비된 배추 절임폐수들을 이용하여 생물학적 산소 요구량(BOD), 화학적 산소요구량(COD), NaCl 농도, pH, 총당 및 환원당 함량, 질소 함량 등의 주요 특성을 분석하였다. 절임폐수의 BOD 및 COD는 표준방법(APHA, AWWA and WPCF(1992), Standard Methods for the Examination of Water and Waste Water, 18th ed., American Public Health Association, Washington, D.C)에 따라 측정하였으며, NaCl 농도는 모어(Mohr)의 방법(AOAC(1995), Official Methods of Analysis, 16th ed., Association of Official Analytic Chemists, Washington, D.C)으로 측정하였다. 환원당 함량은 디니트로살리실산법(dinitrosalicyric acid(DNS) method; Miller, G. L., Anal. Chem., 31, 426∼428(1959))로 측정하였고, 킬달(Kjeldahl) 질소 함량은 표준 방법(APHA, AWWA and WPCF(1992), Standard Methods for the Examination of Water and Waste Water, 18th ed., American Public Health Association, Washington, D.C) 및 A.O.A.C법(AOAC(1995), Official Methods of Analysis, 16th ed., Association of Official Analytic Chemists, Washington, D.C)을 사용하여 측정하였다.Using the cabbage pickled wastewater prepared in (1), the main characteristics such as biological oxygen demand (BOD), chemical oxygen demand (COD), NaCl concentration, pH, total sugar and reducing sugar content, and nitrogen content were analyzed. BOD and COD of pickled wastewater were measured according to standard methods (APHA, AWWA and WPCF (1992), Standard Methods for the Examination of Water and Waste Water, 18th ed., American Public Health Association, Washington, DC). Was measured by Mohr's method (AOAC (1995), Official Methods of Analysis, 16th ed., Association of Official Analytic Chemists, Washington, DC). Reducing sugar content was measured by the dinitrosalicyric acid (DNS) method; Miller, GL, Anal. Chem., 31, 426-428 (1959), and the Kjeldahl nitrogen content was measured by standard methods (APHA, AWWA). and WPCF (1992), Standard Methods for the Examination of Water and Waste Water, 18th ed., American Public Health Association, Washington, DC) and AOAC Act (AOAC (1995), Official Methods of Analysis, 16th ed., Association of Official Analytic Chemists, Washington, DC).
그 결과는 표 1과 같다.The results are shown in Table 1.
김치공장의 절임폐수(A1∼A4)는 pH 5∼6 범위였으며, NaCl 농도는 7∼12%로 매우 높았다. 또한, 환원당 농도는 약 0.5∼1.0 g/ℓ, BOD는 약 1,100∼1,200 mg/ℓ, COD는 1,300∼1,800 mg/ℓ인 것으로 조사되었으며, 총질소함량은 킬달 질소로 20∼28 mg/ℓ로서 상당량의 유기물을 함유한 것으로 나타났다.Pickling wastewater (A1 ~ A4) of the Kimchi plant ranged from pH 5-6, and NaCl concentration was very high (7-12%). In addition, the reducing sugar concentration was about 0.5 to 1.0 g / l, BOD was about 1,100 to 1,200 mg / l, and the COD was 1,300 to 1,800 mg / l, and the total nitrogen content was 20 to 28 mg / l with Kjeldahl nitrogen. It was found to contain significant amounts of organic matter.
이와 같이 김치공장의 절임폐수는 공장에 따라서 성분의 차이가 있는 것으로나타났는데, 이는 원료인 배추의 성분이 시기에 따라 차이가 있으며 소금물의 비율 및 절임 조건을 일정하게 맞추지 못했기 때문으로 볼 수 있다.As such, the pickled wastewater of the Kimchi plant was found to have a difference in ingredients depending on the plant, which may be due to the fact that the ingredients of Chinese cabbage are different depending on the season, and the ratio of the brine and pickling conditions were not consistent.
또한, 실험실에서 제조된 배추 절임폐수를 분석한 결과에서도 pH는 6.2∼6.7 정도였고, NaCl 농도는 6∼7% 부근이었으며, 0.5 g/ℓ 내지 1.1 g/ℓ의 환원당이 함유된 것으로 나타나 김치공장 절임폐수와 그 특성이 유사하였다. 그러나, 1회 절임폐수와 2회 절임폐수를 비교한 결과, 2회 절임폐수는 환원당 함량이 약 50∼100% 가량 증가한 것으로 나타났으며, NaCl 농도는 약 1% 정도 낮아졌다.In addition, the pH of the cabbage pickled wastewater prepared in the laboratory was about 6.2-6.7, NaCl concentration was around 6-7%, and it contained 0.5 g / l to 1.1 g / l reducing sugar. Pickled wastewater and its characteristics were similar. However, as a result of comparing the pickled wastewater to the two times, the pickled wastewater was found to increase the reducing sugar content by about 50 to 100%, and the NaCl concentration was lowered by about 1%.
김치공장의 절임폐수는 알콜 증류 공장의 주정 폐액의 BOD가 수만 mg/ℓ 정도로 매우 높은 것과 비교하면 유기물 함유량이 낮은 수준이지만, BOD가 1,500 mg/ℓ에서 2,500 mg/ℓ인 것으로 조사된(Cho, S. H., et al., J. of Korean Agric. Chem. Soc., 32, 424∼434(1989)) 맥주공장, 과실 통조림공장, 수산물 가공공장의 폐수와는 비슷하였다. 특히, 사우어크라우트 폐염수(Hang, Y. D., et al., J. of Milk and Food Technol., 35, 432∼435(1972))가 NaCl 농도가 3∼4%로 높아 일반 폐수 처리 방법으로 처리하기에 부적합하다고 한 점에 비추어 이보다 NaCl 농도가 훨씬 높은 김치공장의 절임폐수는 기존의 폐수 처리 방법으로는 처리하기 곤란할 것이므로, 단세포 단백질 등으로 이용 가능한 미생물 균체 생산에 이용하는 것이 효과적일 것으로 볼 수 있었다.The pickled wastewater at the Kimchi plant has a low organic matter content compared with the very high BOD of alcoholic liquor in the alcoholic distillation plant, as high as tens of thousands of mg / l. SH, et al., J. of Korean Agric. Chem. Soc., 32, 424-434 (1989)), were similar to wastewater from beer plants, fruit canning plants, and seafood processing plants. In particular, sauerkraut wastewater (Hang, YD, et al., J. of Milk and Food Technol., 35, 432-435 (1972)) has a high NaCl concentration of 3-4%, which can be treated by conventional wastewater treatment methods. In view of the fact that it is not suitable for the pickling wastewater of the Kimchi Plant, which has much higher NaCl concentration than this, it would be difficult to treat by conventional wastewater treatment methods.
실시예 2: 효모균주의 분리, 선발 및 동정Example 2: Isolation, Selection and Identification of Yeast Strains
균주 분리용 시료로 절임폐수, 토양 및 간장, 된장, 고추장 등의 식품을 수집하였다. 균주 분리용 배지로 8%의 NaCl을 첨가한 YM 배지를 사용하고 균분리용 시료를 적당히 희석한 후 평판 도말하여 30℃에서 2∼5일간 배양하였다. 평판 배지에 형성된 콜로니로부터 분리한 70여 주의 효모를 실시예 1에 기재된 표준화된 실험실 제조 배추 절임폐수에 배양하면서 540 nm에서의 흡광도를 측정하여 기존의 알려진 내염성 효모에 비해 생육이 우수한 균주를 선발하였다. 선발된 내염성 효모 균주를 YM 브로쓰에서 2일간 정치배양한 후, 표준화된 실험실 제조 절임폐수 배지에 1% 접종하고 30℃에서 배양한 결과 A9으로 명명된 균주가 가장 우수한 생육을 나타내었다. A9을 바이오로그사(Biolog Inc., Hayward, CA)의 미생물 자동 동정 장치로 분석한 결과, 피키아 귈리어몬디(Pichia guilliermondii)로 동정되었다.As samples for strain isolation, foods such as pickled wastewater, soil and soy sauce, miso, and red pepper paste were collected. YM medium to which 8% NaCl was added as a strain separation medium was used, and the sample for bacterial separation was appropriately diluted and plated and incubated at 30 ° C. for 2 to 5 days. About 70 strains of yeast isolated from colonies formed on the plate medium were cultured in the standardized laboratory-made cabbage pickled wastewater described in Example 1, and the absorbance at 540 nm was measured to select strains superior to the known salt tolerant yeasts. . The selected saline tolerant yeast strains were incubated in YM broth for 2 days, and then inoculated with 1% in a standard laboratory pickled wastewater medium and incubated at 30 ° C. The strain named A9 showed the best growth. A9 was analyzed by Biolog Inc., Hayward, Calif., And identified as Pichia guilliermondii.
이 효모 균주를 피키아 귈리어몬디 A9으로 명명하고, 1999년 2월 18일자로 한국과학기술연구원 생명공학연구소 부설 유전자은행(KCTC)에 기탁번호 제KCTC 8932P호로서 기탁하였다.This yeast strain was named Pichia ceriamondi A9 and was deposited on February 18, 1999 to KCTC (KCTC) affiliated with the Biotechnology Research Institute of Korea Institute of Science and Technology as Accession No. KCTC 8932P.
실시예 3: 절임폐수에서 내염성 효모 피키아 귈리어몬디 A9의 생육 특성Example 3: Growth Characteristics of Salt-Resistant Yeast Pichia Verriamondi A9 in Pickled Wastewater
(1) 최적 배양 온도, pH 및 NaCl 농도의 영향(1) Effect of Optimal Culture Temperature, pH and NaCl Concentration
균체 생산에 적합한 최적 배양온도를 조사하기 위해, pH 6, NaCl 농도 8%로 조절한 표준화된 실험실 제조 배추 절임폐수에 피. 귈리어몬디 A9를 접종한 후 20℃, 25℃, 30℃, 35℃, 40℃의 각 온도에서 180rpm으로 진탕하면서 24시간 배양한 뒤 생육 정도를 측정하여 최적 배양 온도를 결정하였다. 그 결과, 도 1a에서 볼 수 있는 바와 같이, 배양 온도 25℃ 내지 35℃의 범위에서 생육 정도가 높았으며, 가장 우수한 생육을 나타낸 30℃를 최적 배양 온도로 결정하였다.To investigate the optimum incubation temperature suitable for cell production, blood was added to standardized laboratory-made cabbage pickled wastewater adjusted to pH 6, NaCl concentration of 8%. After inoculating Zurimondi A9 and incubated for 24 hours while shaking at 180 rpm at each temperature of 20 ℃, 25 ℃, 30 ℃, 35 ℃, 40 ℃ and then determined the optimal culture temperature by measuring the degree of growth. As a result, as can be seen in Figure 1a, the degree of growth was high in the range of the culture temperature 25 ℃ to 35 ℃, 30 ℃ showing the best growth was determined as the optimum culture temperature.
또한, 균체 생산에 적합한 최적 pH를 검토하기 위해, NaCl 농도를 8%로 하고, pH를 2∼8 범위로 변화시킨 표준화된 실험실 제조 배추 절임폐수에서 피. 귈리어몬디 A9를 30℃에서 180rpm으로 진탕하면서 24시간 배양한 뒤 생육 정도를 측정하여 최적 pH를 결정하였다. 그 결과, 도 1b에서 볼 수 있는 바와 같이, 피. 귈리어몬디 A9는 pH 3 부터 pH 8의 범위에서는 생육 정도에 차이가 극히 적어 생육 범위가 매우 넓었으며, pH 4에서 생육이 가장 높은 것으로 나타났다. 실시예 1에서 확인된 바와 같이 김치공장 절임폐수의 pH는 5 내지 6이었으므로 절임폐수는 pH 조절 없이 균체 생산에 이용할 수 있으나, 본 발명의 균주는 낮은 pH에서도 생육이 우수하므로 절임폐수의 초기 pH를 3∼4 정도로 낮게 조절하여 배양할 경우에는 세균에 의한 오염을 피할 수 있어 유리하다고 볼 수 있다.In addition, in order to examine the optimum pH for cell production, blood was collected from standardized laboratory-made cabbage pickled wastewater with a NaCl concentration of 8% and a pH range of 2-8. The optimum pH was determined by incubating the Zerimondy A9 at 30 ° C. with shaking at 180 rpm for 24 hours and then measuring the growth. As a result, as can be seen in FIG. Zurimondi A9 showed a very wide growth range in the range of pH 3 to pH 8 with very little difference, and showed the highest growth at pH 4. As confirmed in Example 1, the pH of the kimchi factory pickled wastewater was 5 to 6, so the pickled wastewater can be used for cell production without pH adjustment, but the strain of the present invention has excellent growth even at low pH, so the initial pH of the pickled wastewater is When the culture is adjusted to a low level of 3 to 4 it can be seen that it is advantageous to avoid contamination by bacteria.
한편, NaCl 농도를 6∼15%로 변화시킨 pH 6의 표준화된 실험실 제조 배추 절임폐수에 피. 귈리어몬디 A9를 접종한 후 30℃에서 180rpm으로 진탕하면서 24시간 배양한 뒤 생육 정도를 측정하여 절임폐수의 소금농도가 효모의 생육에 미치는 영향을 조사하였다. 그 결과, 도 1c에서 볼 수 있는 바와 같이, 피. 귈리어몬디 A9는 NaCl 농도 9%까지는 영향을 받지 않고 우수한 생육을 보였으며, 10% 이상에서부터는 생육이 약간씩 낮아졌고, 12% 이상에서는 크게 저해되었다. 그러므로, 피. 귈리어몬디 A9는 NaCl 농도가 7∼12%인 절임폐수에서 거의 저해받지 않고 생육할 수 있는 내염성 효모로서 절임폐수에서의 배양에 적합한 균주임을 확인할 수 있었다.Meanwhile, blood was added to a standardized laboratory prepared cabbage pickled wastewater at pH 6 with a change in NaCl concentration of 6-15%. After inoculating Zerimondi A9 and incubating at 180 rpm at 30 ° C for 24 hours, the growth degree was measured to investigate the effect of salt concentration on the growth of yeast. As a result, as can be seen in FIG. Zerimondi A9 showed excellent growth without any influence up to 9% NaCl concentration, slightly lower growth from 10% and significantly inhibited at more than 12%. Therefore, blood. Zurimondi A9 is a saline tolerant yeast that can be grown with little inhibition in pickled wastewater with a NaCl concentration of 7-12%.
(2) 최적 통기량(2) optimum ventilation
균체 생산을 위한 발효조 배양시 최적 통기량을 조사하기 위해, NaCl 농도를 8%로, 초기 pH를 4로 조절한 표준화된 실험실 제조 배추 절임폐수에, 5%의 NaCl을 첨가한 YM 브로쓰에서 18시간동안 180 rpm에서 진탕 배양한 피. 귈리어몬디 A9를 2% 접종한 후, 발효조의 발효용량을 1ℓ로 하고 교반속도를 300 rpm으로 고정한 다음, 통기량을 0.5 vvm, 1.0 vvm, 2.0 vvm으로 조절하여 배양하면서 생육을 비교하였다.To investigate the optimal aeration in fermenter culture for cell production, the standardized laboratory cabbage pickled wastewater with 8% NaCl and an initial pH of 4 was added to YM broth containing 5% NaCl. Blood incubated at 180 rpm for an hour. After inoculating 2% of Zurimondi A9, the fermentation capacity of the fermenter was set to 1 L, the stirring speed was fixed at 300 rpm, and the growth rate was adjusted to 0.5 vvm, 1.0 vvm, 2.0 vvm, and the growth was compared.
그 결과, 효모의 생육은 생육속도 및 정도에서 통기량에 따라 거의 차이가 없어 0.5 vvm의 통기량으로도 충분한 것으로 나타났다(도 2).As a result, the growth of yeast is almost no difference depending on the amount of aeration in the growth rate and degree, it was found that even with a ventilation amount of 0.5 vvm (Fig. 2).
(3) 암모늄염, 인산염 및 미량원소의 첨가 효과(3) Effect of Addition of Ammonium Salt, Phosphate and Trace Elements
절임폐수는 다른 식품 공장의 폐수에 비하여 탄소원을 비롯한 균체 생육에 필요한 영양분 함량이 낮은 편이므로 피. 귈리어몬디 A9 배양시 소량의 암모늄염 및 인산염을 첨가하여 균체 생산량의 증가 효과를 조사하였다. 구체적으로, pH 4.0, NaCl 농도 8%인 표준화된 실험실 제조 배추 절임폐수에 (NH4)2SO4와 K2HPO4를 각각 0%, 0.2% 및 0.5%로 첨가한 후 피. 귈리어몬디 A9를 접종하고 30℃에서 180rpm으로 24시간 진탕 배양하면서 생육 정도를 측정하여 암모늄염 및 인산염의 첨가에 의한 균체 생산 증가 효과를 조사하였다. 그 결과, 도 3a 및 3b에서 볼 수 있는 바와 같이, (NH4)2SO4및 K2HPO4는0.5%까지 첨가하여도 대조군에 비해 유의성 있는 차이를 보이지 않았다.Pickled waste water has a lower nutrient content than the other food factories' waste water, which is required for growth of cells including carbon sources. A small amount of ammonium salt and phosphate was added to the culture of Zurimondi A9 to investigate the effect of increasing the cell production. Specifically, after adding (NH 4 ) 2 SO 4 and K 2 HPO 4 to 0%, 0.2% and 0.5%, respectively, in a standard laboratory cabbage pickled wastewater with pH 4.0 and 8% NaCl concentration, p. Inoculation with Zurimondi A9 and shaking growth at 180 ℃ at 30 ℃ for 24 hours to measure the growth of the cell production was investigated by the addition of ammonium salt and phosphate. As a result, as can be seen in Figures 3a and 3b, (NH 4 ) 2 SO 4 and K 2 HPO 4 did not show a significant difference compared to the control even when added up to 0.5%.
한편, 미량원소로 구리(CuSO4), 망간(MnSO4), 마그네슘(MgSO4), 칼슘(CaSO4), 철(FeSO4), 아연(ZnSO4) 등을 0.5 mM의 농도로 상기 절임폐수에 첨가한 후 피. 귈리어몬디 A9를 30℃에서 24시간 배양하여 균체 생산 증가 효과를 조사하였다. 그 결과는 도 4에 나타내었으며, 여기에서 1은 미량원소를 첨가하지 않은 대조군이고 2 내지 7은 미량원소로 CuSO4, MnSO4, MgSO4, CaSO4, FeSO4및 ZnSO4를 각각 첨가한 시험군이다. 도 4에서 볼 수 있는 바와 같이, ZnSO4가 약간의 증가효과를 보였으며 그 이외는 효과가 없었다. ZnSO4의 최적 첨가 농도를 결정하기 위해, ZnSO4를 0 내지 5mM 농도로 첨가한 절임폐수에서 피. 귈리어몬디 A9를 배양하여 생육정도를 조사한 결과, 도 5에서와 같이 0.5 mM에서 가장 생육이 높았으며 1mM보다 높은 농도에서는 생육 저해를 나타내었다. 그러나, 0.5 mM의 ZnSO4의 첨가에 의한 균체 증가 효과는 크지 않으므로 첨가하지 않아도 무방하다.Meanwhile, copper (CuSO) as a trace element4), Manganese (MnSO4), Magnesium (MgSO4), Calcium (CaSO4), Iron (FeSO4), Zinc (ZnSO4) And then added to the pickled wastewater at a concentration of 0.5 mM. In Vilermondi A9 was incubated for 24 hours at 30 ℃ to investigate the effect of increasing the cell production. The results are shown in Figure 4, where 1 is a control group without addition of trace elements and 2 to 7 CuSO as a trace element.4, MnSO4, MgSO4, CaSO4, FeSO4And ZnSO4It is the test group which added each. As can be seen in Figure 4, ZnSO4Showed a slight increase, but there was no effect. ZnSO4In order to determine the optimal concentration of addition, ZnSO4Blood in pickled wastewater added at 0-5 mM concentration. As a result of culturing Zerimondi A9, the growth was the highest at 0.5 mM as shown in FIG. However, 0.5 mM ZnSO4The effect of cell growth by the addition of is not so great that it is not necessary to add.
실시예 4: BOD 제거 효과Example 4: BOD Removal Effect
실시예 1에 기재된 표준화된 실험실 제조 배추 절임폐수에 피. 귈리어몬디 A9를 배양하였을 때 절임폐수의 BOD 변화를 측정하여 효모 배양 처리에 의한 유기물 제거 효과를 조사하였다.Blood to the standardized laboratory prepared cabbage pickled wastewater described in Example 1. The change of BOD in pickled wastewater was measured when culturing Zurimondi A9 to investigate the effect of organic matter removal by yeast culture treatment.
NaCl 농도를 8%로, 초기 pH를 4로 조절한 절임 폐수에 피. 귈리어몬디 A9를 1% 접종하고 30℃에서 180 rpm으로 진탕 배양하면서 BOD 감소 효과를 조사하였다. 그 결과, 배양 초기 BOD가 1,200 mg/ℓ이었던 절임폐수는 24시간 이내에 BOD가 120 mg/ℓ로 감소하였다.Blood in pickled wastewater with an adjusted NaCl concentration of 8% and an initial pH of 4. The effect of BOD reduction was investigated by inoculating 1% of ZeriMondi A9 and shaking culture at 180 rpm at 30 ° C. As a result, the pickled wastewater, which had an initial BOD of 1,200 mg / l, decreased to 120 mg / l of BOD within 24 hours.
이와 같이 절임폐수의 BOD를 약 90% 이상 제거시킨 결과는 절간 고구마원료 주정 폐액에 토룰롭시스 칸디다 (Tolulopsis candida) 배양시 38.9%의 BOD를 감소시킨 이 등(Lee, H. Y., et al., Kor. J. Appl. Microbiol. Bioeng., 10, 95∼100(1982))의 결과에 비해서는 훨씬 높고, 주정 공장 폐수에 아스퍼질러스 푸미가투스(Aspergillus fumigatus)를 배양하여 94%의 BOD를 제거한 조 등(Cho, S. H., et al., J. of Korean Agric. Chem. Soc., 32, 424∼434(1989))의 결과와 사우어크라우트 폐염수에 칸디다 유틸리스를 배양하여 90% 이상의 BOD를 제거한 행의 결과(Hang, Y. D., et al., Progress in Water Technol., 8, 381∼384(1976))와는 비슷한 정도이다.As a result of removing more than 90% of the BOD in pickled wastewater, Lee, HY, et al., Kor, who reduced 38.9% of BOD in Tolulopsis candida culture in the interlaced sweet potato raw liquor liquor J. Appl.Microbiol.Bioeng., 10, 95-100 (1982)), much higher than that of 94% BOD by culturing Aspergillus fumigatus in brewery wastewater. Results of Cho et al. (Cho, SH, et al., J. of Korean Agric. Chem. Soc., 32, 424-434 (1989)) and cultured Candida utility in Sourkraut waste saline to obtain more than 90% BOD. This is similar to the result of the removed row (Hang, YD, et al., Progress in Water Technol., 8, 381-384 (1976)).
실시예 5: 균체의 성분 분석Example 5: Component Analysis of Cells
NaCl 농도 8%, 초기 pH 4로 조절한 절임폐수에 피. 귈리어몬디 A9를 접종하고 30℃에서 180 rpm으로 진탕하면서 24시간 동안 배양하였다. 배양액을 원심분리하여 균체를 회수하고 증류수로 2회 세척한 후 동결 건조하여 건조 균체를 얻고, 단백질, 지질, 탄수화물 및 회분함량을 조사하였다. 건조 균체의 조단백질 함량은 마이크로-킬달법 (micro-Kjeldahl method; APHA, AWWA and WPCF(1992), Standard methods for the examination of water and waste water, 18th ed., American Public Health Association, Washington, D.C)으로, 탄수화물 함량은 페놀-황산법(Dubois, M., et al., Anal. Chem., 28, 350∼356(1956))으로 측정하였으며, 조지방 함량은 블리히와 다이어의 방법(Bligh, E. G. and W. J. Dyer, Can. J. Biochem. Physiol., 37, 911∼917(1959))에 따라 측정하였다. 회분 함량은 시료를 항량을 알고 있는 도가니에 넣고 무게를 측정한 후 전기로에 넣고 500℃에서 수시간 태운 다음 데시케이터(desiccator)에 옮겨 방냉한 후 실온에서 평량하였다. 항량에 이를 때까지 반복하여 회분 함량을 계산하였다.Blood in pickled wastewater adjusted to 8% NaCl, initial pH 4. Inoculated with ZeriMondi A9 and incubated for 24 hours while shaking at 180 rpm at 30 ℃. The culture solution was centrifuged to recover the cells, washed twice with distilled water and lyophilized to obtain dried cells, and the protein, lipid, carbohydrate and ash content were investigated. Crude protein content of dry cells was determined by the micro-Kjeldahl method (APHA, AWWA and WPCF (1992), Standard methods for the examination of water and waste water, 18th ed., American Public Health Association, Washington, DC). The carbohydrate content was measured by the phenol-sulfuric acid method (Dubois, M., et al., Anal. Chem., 28, 350-356 (1956)), and the crude fat content was the method of Bligh, EG and WJ. Dyer, Can. J. Biochem. Physiol., 37, 911-917 (1959)). The ash content was placed in a crucible of known quantity, weighed, placed in an electric furnace, burned for several hours at 500 ° C., and then cooled to room temperature after being transferred to a desiccator. The ash content was calculated by repeating until the dosage was reached.
효모 균체의 성분 분석 결과는 표 2에 나타낸 바와 같고, 절임폐수에서 배양된 효모의 균체 성분 조성을 영양배지인 YM 브로쓰에서 동일한 조건으로 배양한 경우와 비교하면 단백질 함량은 약 6% 적으며, 지질 함량은 약 6% 많고, 회분함량은 동일하였다.The results of the analysis of the components of the yeast cells are shown in Table 2, and the protein content of the yeast cells cultured in pickled wastewater was about 6% less than that of the culture medium under the same conditions in YM broth, a nutrient medium, and lipids The content was about 6% and the ash content was the same.
이 결과는 절간 고구마 주정폐액에서 배양한 토룰롭시스 칸디다(Lee, H. Y., et al., Kor. J. Appl. Microbiol. Bioeng., 10, 95∼100(1982))의 단백질 함량이 48%인 것과 비교하면 적은 편이나, 치즈 유청액에서 배양한 사카로마이세스 프래질리스(Saccharomyces fragilis) 등의 효모가 30∼40.25%(El-Samragy, T. A., et al., Process Biocem. 23, 28∼30(1988)), 칸디다 귈리어몬디(Candida guilliermondii)를 탄화수소에 배양했을 때 26.7%인 것(Sabry, S. A., et al., Biomed. Lett. 46, 615∼618(1991))에 비하면 훨씬 높은 것으로 나타났다.This result showed that 48% of Tolulopsis Candida (Lee, HY, et al., Kor. J. Appl. Microbiol. Bioeng., 10, 95-100 (1982)) was cultured in interlaced sweet potato alcoholic liquor. Compared to that of Saccharomyces fragilis, 30-40.25% (El-Samragy, TA, et al., Process Biocem. 23, 28-30) (1988), which is much higher than Candida guilliermondii, which is 26.7% when cultured in hydrocarbon (Sabry, SA, et al., Biomed. Lett. 46, 615-618 (1991)). appear.
실시예 6: 배추 쓰레기 착즙 첨가 효과Example 6: Chinese cabbage trash juice addition effect
김치 원료인 배추를 다듬는 과정에서는 약 10% 이상의 배추 쓰레기가 발생하며 배추에는 효모 등의 미생물이 쉽게 이용이 가능한 당이 1.6∼2.6% 함유되어 있으므로(Shim, S. T., et al., Korean J. Food Sci. Technol., 22, 278∼284(1990); 및 Yu, H. G., et al., Korean J. Food Sci. Technol., 24, 107∼110(1992)), 김치공장에서 상당량 발생되는 배추 쓰레기는 미생물 배지로 이용 가치가 매우 높은 우수한 유기성 폐기물 자원이라 할 수 있다. 그러므로, 본 실시예에서는 김치공장에서 김치 제조시 다량 발생되어 처리에 곤란을 겪고 있는 배추 쓰레기를 절임폐수에 첨가하여 효모의 생육을 증가시키는 방법을 시도하였다.During the process of trimming Chinese cabbage, which is a kimchi raw material, more than 10% of Chinese cabbage waste is generated, and since the cabbage contains 1.6-2.6% of sugars that can be easily used by microorganisms such as yeast (Shim, ST, et al., Korean J. Food Sci. Technol., 22, 278-284 (1990); and Yu, HG, et al., Korean J. Food Sci. Technol., 24, 107-110 (1992)) Is an excellent organic waste resource with very high value as a microbial medium. Therefore, in the present embodiment, a method of increasing the growth of yeast by adding cabbage waste, which is difficult to process due to a large amount of kimchi production during kimchi production, was added to the pickled wastewater.
김치 제조시 배추를 다듬는 과정에서 발생한 배추 쓰레기를 모아 블렌더(Waring blender)로 파쇄하고, 가제로 걸러 배추 쓰레기 착즙액을 얻었다. 배추 쓰레기의 착즙액을 NaCl 농도 8%, 초기 pH 4로 조절한 표준화된 실험실 제조 배추 절임폐수에 각각 5%, 10%, 20% 및 30%의 비율로 첨가하고 피. 귈리어몬디 A9를 접종하여 30℃에서 180rpm으로 진탕 배양하면서 균체 생산량을 측정하였다. 균체 생산량은 균 배양액을 일정량 취한 후 원심분리(4,000 rpm, 15분)하여 균체를 얻고 증류수로 세척한 뒤 다시 원심분리하여 회수한 균체를 105℃ 건조기에서 항량에 도달 할 때까지 건조하여 측정하였다.The cabbage waste generated during the process of trimming cabbage during kimchi production was collected and crushed with a blender (Waring blender), and filtered to obtain cabbage waste juice. Juices of Chinese cabbage waste were added to standardized laboratory cabbage pickled wastewater adjusted to 8% NaCl and initial pH 4 at 5%, 10%, 20% and 30%, respectively. Cell inoculum was measured by inoculating Varianmondi A9 and shaking culture at 180 ° C at 30 ° C. Cell production was measured by taking a certain amount of the culture medium, centrifuged (4,000 rpm, 15 minutes) to obtain the cells, washed with distilled water and centrifuged again and dried until the cell reaches a constant in 105 ℃ dryer.
그 결과는 표 3에 나타내었으며, 표 3에서 볼 수 있는 바와 같이, 배추 쓰레기를 첨가하지 않은 경우 최고 균체 생산량은 0.69 g/ℓ이었으나, 배추 쓰레기 착즙액 첨가에 의해 건조균체량은 10% 첨가시 1.87 g/ℓ, 20% 첨가시 2.75 g/ℓ, 30% 첨가시 3.4 g/ℓ에 달해 첨가하지 않은 경우에 비해 각각 2.7배, 4.0배 및 4.9배 증가하여 절임폐수만 사용한 경우보다 균체 생산량이 크게 증가하였다. 이때, 환원당은 5%, 10% 및 20% 첨가시에는 24시간, 30% 첨가시에는 48시간 이내에 완전히 소모되었다.The results are shown in Table 3. As can be seen in Table 3, when the Chinese cabbage waste was not added, the maximum cell production was 0.69 g / L, but the dry cell weight was 1.87 when the cabbage waste juice was added. g / l, 20% added 2.75 g / l, 30% added 3.4 g / l, 2.7 times, 4.0 times and 4.9 times increased, respectively, compared to the case without addition, the cell production is greater than the use of pickled waste water only Increased. At this time, reducing sugar was completely consumed within 24 hours when 5%, 10% and 20% were added, and within 48 hours when 30% was added.
따라서, 김치공장에서 다량 발생되어 문제가 되고 있는 또 다른 폐기물인 배추 쓰레기를 김치공장 절임폐수에 첨가하는 방법으로 효모 균체 생산에 이용함으로써 두 종류의 폐기물을 동시에 효과적으로 처리할 수 있다.Therefore, by adding a large amount of cabbage waste, which is a problem in the Kimchi factory, added to the pickled waste water of the Kimchi factory, the two types of waste can be effectively treated simultaneously.
실시예 7: 배추 절임폐수에서 피키아 귈리어몬디 A9와 몇 가지 내염성 효모의 생육정도 비교Example 7: Growth of Pichia verriamondi A9 and some salt tolerant yeasts in Chinese cabbage pickled wastewater
본 발명의 균주 피. 귈리어몬디 A9와 동일 종으로 알려진 피키아 귈리어몬디 ATCC 6260의 절임폐수에서의 BOD 제거 효과를 실시예 4에 기재된 방법으로 조사하고, 본 발명의 균주 피. 귈리어몬디 A9와 비교하였다. 피. 귈리어몬디 ATCC 6260의 절임폐수 BOD 제거율은 86%로서 90%를 나타낸 A9보다 BOD 제거 효과가 약하기는 하지만 매우 우수하였다.Strain P of the Invention. The effect of BOD removal in pickled wastewater of Pichia verriamondi ATCC 6260, which is known to be the same species as VeriMondi A9, was investigated by the method described in Example 4, and strain P of the present invention. Comparison was made with Zerimondi A9. blood. The removal rate of BOD of pickled wastewater was 86%, which was weaker than A9, which was 90%.
한편, 본 발명의 피. 귈리어몬디 A9, 이와 동종인 피. 귈리어몬디 ATCC 6260 및 내염성 효모인 칸디다 할로니트라토필라(Candida halonitratophila) IFO 1595, 자이고사카로마이세스 룩씨(Zygosaccharomyces rouxii) KFRI 204, 및 칸디다 버사틸리스(Candida versatilis) IFO 1228을 이용하여 실시예 4의 방법으로 배추 절임 폐수에서의 생육 정도를 조사하였다. 그 결과, 도 7에서 볼 수 있는 바와 같이, 피. 귈리어몬디 ATCC 6260의 최고 생육 정도는 30℃에서 배양할 경우 540 nm에서의 흡광도 값이 1.3으로서 피. 귈리어몬디 A9의 최고 생육 정도의 90% 수준이었다. 특히, 배양 온도가 높아짐에 따라 생육정도의 차이가 커져 40℃ 배양의 경우 피. 귈리어몬디 ATCC 6260의 24시간 배양 후 생육 정도는 A9의 생육 정도의 21 % 수준이었다. 즉, 40℃ 배양의 경우는 본 발명의 균주 A9은 ATCC 6260보다 약 4.6배 우수하였다. 본 발명의 균주 피. 귈리어몬디 A9의 고온에서도 생육이 우수한 특성은 일반적으로 공업적인 미생물 배양시 발생하는 발효열에 의한 온도 상승에 대한 냉각비용을 절감할 수 있다는 측면에서 공업적으로 매우 유리한 특성이다. 또한, 본 발명의 균주 피. 귈리어몬디 A9은 기타 내염성 균주들과 비교하여 배추 절임폐수에서의 생육이 훨씬 우수하였다.Meanwhile, the blood of the present invention. Zerimondi A9, blood of this kind. Examples using Zulmondi ATCC 6260 and flame resistant yeast Candida halonitratophila IFO 1595, Zygosaccharomyces rouxii KFRI 204, and Candida versatilis IFO 1228 The growth of the cabbage pickled wastewater was investigated by the method of 4. As a result, as can be seen in FIG. The highest growth level of Zerimondy ATCC 6260 was found to be 1.3 when absorbed at 540 nm when incubated at 30 ° C. It was 90% of the maximum growth level of ZeriMondi A9. In particular, as the incubation temperature increases, the difference in growth degree is increased. After 24 hours of incubation with Zerimondi ATCC 6260, the degree of growth was 21% of that of A9. That is, in the case of 40 ° C. culture, strain A9 of the present invention was about 4.6 times better than ATCC 6260. Strain P of the Invention. The excellent growth characteristics of Zurimondi A9 are very industrially advantageous in that the cooling cost of the temperature rise due to the fermentation heat generated during the culture of industrial microorganisms can be reduced. Also, strain P. of the present invention. Varianmondi A9 was much better in the Chinese cabbage pickled waste compared to other salt resistant strains.
그러나, 피. 귈리어몬디 ATCC 6260도 배추 절임 폐수에서 상당히 우수한 생육과 BOD 제거 효과를 나타내므로, 본 발명의 균주 피. 귈리어몬디 A9와 동일 종의 균주들은 배추 절임 폐수에서의 균체 생산에 적합한 것으로 밝혀졌다.However, blood. Zerimondi ATCC 6260 also shows a very good growth and BOD removal effect in pickled cabbage wastewater, strain of the present invention. Strains of the same species as Zurimondi A9 were found to be suitable for the production of cells in Chinese cabbage pickled wastewater.
본 발명의 균주는 18%의 NaCl이 함유된 환경에서도 생육이 가능한 내염성 효모로서 고농도(7-12%)의 NaCl을 함유하는 배추 절임 폐수에서 생육이 가능하며 배추 절임 폐수에 함유된 유기물 이용 능력이 우수하여 상기 균주를 배추 절임 폐수에 배양함으로써 단세포 단백질을 효과적으로 생산하면서 동시에 유기물을 제거 할 수 있다. 상기 균주 A9은 배추 절임 폐수에서의 생육 pH, 생육 온도 및 생육 염농도 범위가 넓은 균주이므로 상이한 절임 공정에 따른 절임 폐수 성분의 차이에 대한 부가적인 처리가 불필요하다. 또한, 피. 귈리어몬디를 염이 함유된 폐기물에서 배양함으로써 균체를 생산함과 동시에 폐기물도 처리할 수 있다. 구체적인 예로 본 발명의 방법은 김치 제조 공장의 절임 폐수 및 폐기물, 절임채소 가공공장(피클류, 단무지 생산 공장 등)의 절임 폐수 및 폐기물, 장류 가공 폐수 및 폐기물, 수산물 염장 가공 폐수 및 폐기물, 염장 육가공(햄 등) 폐수 및 폐기물의 처리에 사용할 수 있다. 특히, 배추 절임 폐수의 경우, 배추 쓰레기 착즙액을 절임폐수에 첨가하여 피. 귈리어몬디를 배양하면 균체생산량이 크게 증가하며, 김치공장에서 발생하는 두가지의 폐기물을 동시에 효과적으로 처리할 수 있다.The strain of the present invention is a salt-tolerant yeast capable of growing even in an environment containing 18% NaCl, which can be grown in pickled wastewater containing NaCl of high concentration (7-12%), and has the ability to use organic matter contained in the pickled wastewater. Excellent by culturing the strain in the Chinese cabbage pickled waste water can effectively produce a single-cell protein while at the same time remove the organic matter. Since the strain A9 is a strain having a wide range of growth pH, growth temperature and growth salt concentration in the Chinese cabbage pickling wastewater, it is unnecessary to perform additional treatment for the difference in pickling wastewater components according to different pickling processes. Also, p. By culturing Curiarmond in wastes containing salt, it is possible to produce cells and process wastes. As a specific example, the method of the present invention can be used for pickling wastewater and waste in kimchi manufacturing plant, pickled vegetable processing plant (pickles, radish production plant, etc.) (Ham, etc.) can be used for the treatment of waste water and waste. In particular, in the case of cabbage pickled wastewater, the cabbage waste juice is added to the pickled wastewater to avoid blood. Cultivation of vitreous mondy greatly increases cell production, and can effectively treat two kinds of wastes from the Kimchi plant at the same time.
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CN106190875A (en) * | 2016-07-13 | 2016-12-07 | 江西沃邦兴环保科技有限公司 | Facultative Halophiles bacterial strain under a kind of high-salt tolerance environment and screening technique thereof and application |
CN106190875B (en) * | 2016-07-13 | 2019-05-10 | 江西沃邦兴环保科技有限公司 | Salt tolerant bacteria strain and its screening technique and application under a kind of high-salt tolerance environment |
CN112501038A (en) * | 2020-11-11 | 2021-03-16 | 大连海洋大学 | Pichia guilliermondii and method for treating high-salinity wastewater |
CN112501038B (en) * | 2020-11-11 | 2024-02-02 | 大连海洋大学 | Pichia guilliermondii and method for treating high-salt wastewater |
CN114804336A (en) * | 2022-01-20 | 2022-07-29 | 辽宁师范大学 | Device and method for reducing membrane pollution of membrane bioreactor |
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