JPH0522506B2 - - Google Patents
Info
- Publication number
- JPH0522506B2 JPH0522506B2 JP12821886A JP12821886A JPH0522506B2 JP H0522506 B2 JPH0522506 B2 JP H0522506B2 JP 12821886 A JP12821886 A JP 12821886A JP 12821886 A JP12821886 A JP 12821886A JP H0522506 B2 JPH0522506 B2 JP H0522506B2
- Authority
- JP
- Japan
- Prior art keywords
- culture
- tank
- bacteria
- anaerobic bacteria
- bacterial
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Expired - Lifetime
Links
- 239000000706 filtrate Substances 0.000 claims abstract description 45
- 239000002609 medium Substances 0.000 claims abstract description 34
- 239000007788 liquid Substances 0.000 claims abstract description 21
- 239000000126 substance Substances 0.000 claims abstract description 19
- 239000010815 organic waste Substances 0.000 claims abstract description 11
- 239000001963 growth medium Substances 0.000 claims abstract description 6
- 239000000203 mixture Substances 0.000 claims abstract description 6
- 230000001580 bacterial effect Effects 0.000 claims description 68
- 241001148471 unidentified anaerobic bacterium Species 0.000 claims description 55
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 claims description 48
- 239000001301 oxygen Substances 0.000 claims description 48
- 229910052760 oxygen Inorganic materials 0.000 claims description 48
- 238000012546 transfer Methods 0.000 claims description 33
- 239000002002 slurry Substances 0.000 claims description 30
- 241001148470 aerobic bacillus Species 0.000 claims description 23
- 238000012258 culturing Methods 0.000 claims description 23
- 238000003860 storage Methods 0.000 claims description 18
- 241000894006 Bacteria Species 0.000 claims description 16
- 238000000034 method Methods 0.000 claims description 16
- 239000000758 substrate Substances 0.000 claims description 3
- 230000001568 sexual effect Effects 0.000 claims 1
- 239000011261 inert gas Substances 0.000 abstract description 6
- 230000000813 microbial effect Effects 0.000 abstract description 3
- 239000000047 product Substances 0.000 abstract description 3
- 239000000463 material Substances 0.000 abstract 1
- 239000007789 gas Substances 0.000 description 48
- CSNNHWWHGAXBCP-UHFFFAOYSA-L Magnesium sulfate Chemical compound [Mg+2].[O-][S+2]([O-])([O-])[O-] CSNNHWWHGAXBCP-UHFFFAOYSA-L 0.000 description 24
- 230000001954 sterilising effect Effects 0.000 description 21
- IJGRMHOSHXDMSA-UHFFFAOYSA-N Atomic nitrogen Chemical compound N#N IJGRMHOSHXDMSA-UHFFFAOYSA-N 0.000 description 20
- 238000004659 sterilization and disinfection Methods 0.000 description 20
- 238000005273 aeration Methods 0.000 description 18
- LWIHDJKSTIGBAC-UHFFFAOYSA-K potassium phosphate Substances [K+].[K+].[K+].[O-]P([O-])([O-])=O LWIHDJKSTIGBAC-UHFFFAOYSA-K 0.000 description 14
- 230000000052 comparative effect Effects 0.000 description 12
- 239000002054 inoculum Substances 0.000 description 12
- 229910052943 magnesium sulfate Inorganic materials 0.000 description 12
- 235000019341 magnesium sulphate Nutrition 0.000 description 12
- 229910052757 nitrogen Inorganic materials 0.000 description 10
- 238000009423 ventilation Methods 0.000 description 10
- 241000193403 Clostridium Species 0.000 description 9
- 229920002472 Starch Polymers 0.000 description 9
- 229940041514 candida albicans extract Drugs 0.000 description 9
- 230000004663 cell proliferation Effects 0.000 description 9
- 238000001816 cooling Methods 0.000 description 9
- 238000000855 fermentation Methods 0.000 description 9
- 230000004151 fermentation Effects 0.000 description 9
- 235000019698 starch Nutrition 0.000 description 9
- 239000008107 starch Substances 0.000 description 9
- 239000012138 yeast extract Substances 0.000 description 9
- 230000012010 growth Effects 0.000 description 8
- 239000003595 mist Substances 0.000 description 7
- 229910000160 potassium phosphate Inorganic materials 0.000 description 6
- 235000011009 potassium phosphates Nutrition 0.000 description 6
- 229910000162 sodium phosphate Inorganic materials 0.000 description 6
- 239000001488 sodium phosphate Substances 0.000 description 6
- 235000011008 sodium phosphates Nutrition 0.000 description 6
- 239000007787 solid Substances 0.000 description 6
- RYFMWSXOAZQYPI-UHFFFAOYSA-K trisodium phosphate Chemical compound [Na+].[Na+].[Na+].[O-]P([O-])([O-])=O RYFMWSXOAZQYPI-UHFFFAOYSA-K 0.000 description 6
- 241000665753 Clostridia bacterium Species 0.000 description 5
- 235000015097 nutrients Nutrition 0.000 description 5
- 229910001220 stainless steel Inorganic materials 0.000 description 5
- 239000010935 stainless steel Substances 0.000 description 5
- 239000002912 waste gas Substances 0.000 description 5
- 239000002699 waste material Substances 0.000 description 5
- 238000012136 culture method Methods 0.000 description 4
- VNWKTOKETHGBQD-UHFFFAOYSA-N methane Chemical compound C VNWKTOKETHGBQD-UHFFFAOYSA-N 0.000 description 4
- CWERGRDVMFNCDR-UHFFFAOYSA-N thioglycolic acid Chemical compound OC(=O)CS CWERGRDVMFNCDR-UHFFFAOYSA-N 0.000 description 4
- 244000063299 Bacillus subtilis Species 0.000 description 3
- 235000014469 Bacillus subtilis Nutrition 0.000 description 3
- BNIILDVGGAEEIG-UHFFFAOYSA-L disodium hydrogen phosphate Chemical compound [Na+].[Na+].OP([O-])([O-])=O BNIILDVGGAEEIG-UHFFFAOYSA-L 0.000 description 3
- 229910000397 disodium phosphate Inorganic materials 0.000 description 3
- 235000019800 disodium phosphate Nutrition 0.000 description 3
- 230000000694 effects Effects 0.000 description 3
- 238000011534 incubation Methods 0.000 description 3
- 238000009630 liquid culture Methods 0.000 description 3
- 230000035755 proliferation Effects 0.000 description 3
- 238000010926 purge Methods 0.000 description 3
- 238000000926 separation method Methods 0.000 description 3
- 238000003756 stirring Methods 0.000 description 3
- XKRFYHLGVUSROY-UHFFFAOYSA-N Argon Chemical compound [Ar] XKRFYHLGVUSROY-UHFFFAOYSA-N 0.000 description 2
- 241000193830 Bacillus <bacterium> Species 0.000 description 2
- 241000588724 Escherichia coli Species 0.000 description 2
- 229940123973 Oxygen scavenger Drugs 0.000 description 2
- 239000006227 byproduct Substances 0.000 description 2
- 239000003638 chemical reducing agent Substances 0.000 description 2
- 238000000605 extraction Methods 0.000 description 2
- 238000011049 filling Methods 0.000 description 2
- 239000013028 medium composition Substances 0.000 description 2
- 229910000402 monopotassium phosphate Inorganic materials 0.000 description 2
- 235000019796 monopotassium phosphate Nutrition 0.000 description 2
- GNSKLFRGEWLPPA-UHFFFAOYSA-M potassium dihydrogen phosphate Chemical compound [K+].OP(O)([O-])=O GNSKLFRGEWLPPA-UHFFFAOYSA-M 0.000 description 2
- 238000011160 research Methods 0.000 description 2
- 239000010802 sludge Substances 0.000 description 2
- 241000186000 Bifidobacterium Species 0.000 description 1
- RWSOTUBLDIXVET-UHFFFAOYSA-N Dihydrogen sulfide Chemical compound S RWSOTUBLDIXVET-UHFFFAOYSA-N 0.000 description 1
- MYMOFIZGZYHOMD-UHFFFAOYSA-N Dioxygen Chemical compound O=O MYMOFIZGZYHOMD-UHFFFAOYSA-N 0.000 description 1
- 240000004808 Saccharomyces cerevisiae Species 0.000 description 1
- 241000297434 Stenotarsus subtilis Species 0.000 description 1
- 239000002253 acid Substances 0.000 description 1
- 150000001447 alkali salts Chemical class 0.000 description 1
- 230000003698 anagen phase Effects 0.000 description 1
- 229910052786 argon Inorganic materials 0.000 description 1
- 238000012865 aseptic processing Methods 0.000 description 1
- 238000007664 blowing Methods 0.000 description 1
- 230000010261 cell growth Effects 0.000 description 1
- 239000012531 culture fluid Substances 0.000 description 1
- 230000007423 decrease Effects 0.000 description 1
- 230000003247 decreasing effect Effects 0.000 description 1
- 238000010586 diagram Methods 0.000 description 1
- 229910001882 dioxygen Inorganic materials 0.000 description 1
- ZPWVASYFFYYZEW-UHFFFAOYSA-L dipotassium hydrogen phosphate Chemical compound [K+].[K+].OP([O-])([O-])=O ZPWVASYFFYYZEW-UHFFFAOYSA-L 0.000 description 1
- 238000002474 experimental method Methods 0.000 description 1
- 238000001914 filtration Methods 0.000 description 1
- 229910000037 hydrogen sulfide Inorganic materials 0.000 description 1
- 230000006698 induction Effects 0.000 description 1
- 238000011081 inoculation Methods 0.000 description 1
- 238000004519 manufacturing process Methods 0.000 description 1
- 230000004060 metabolic process Effects 0.000 description 1
- 230000001766 physiological effect Effects 0.000 description 1
- 230000002265 prevention Effects 0.000 description 1
- 239000002994 raw material Substances 0.000 description 1
- 238000011218 seed culture Methods 0.000 description 1
- 238000004904 shortening Methods 0.000 description 1
- GNBVPFITFYNRCN-UHFFFAOYSA-M sodium thioglycolate Chemical compound [Na+].[O-]C(=O)CS GNBVPFITFYNRCN-UHFFFAOYSA-M 0.000 description 1
- 229940046307 sodium thioglycolate Drugs 0.000 description 1
Classifications
-
- C—CHEMISTRY; METALLURGY
- C12—BIOCHEMISTRY; BEER; SPIRITS; WINE; VINEGAR; MICROBIOLOGY; ENZYMOLOGY; MUTATION OR GENETIC ENGINEERING
- C12M—APPARATUS FOR ENZYMOLOGY OR MICROBIOLOGY; APPARATUS FOR CULTURING MICROORGANISMS FOR PRODUCING BIOMASS, FOR GROWING CELLS OR FOR OBTAINING FERMENTATION OR METABOLIC PRODUCTS, i.e. BIOREACTORS OR FERMENTERS
- C12M29/00—Means for introduction, extraction or recirculation of materials, e.g. pumps
- C12M29/02—Percolation
-
- C—CHEMISTRY; METALLURGY
- C12—BIOCHEMISTRY; BEER; SPIRITS; WINE; VINEGAR; MICROBIOLOGY; ENZYMOLOGY; MUTATION OR GENETIC ENGINEERING
- C12M—APPARATUS FOR ENZYMOLOGY OR MICROBIOLOGY; APPARATUS FOR CULTURING MICROORGANISMS FOR PRODUCING BIOMASS, FOR GROWING CELLS OR FOR OBTAINING FERMENTATION OR METABOLIC PRODUCTS, i.e. BIOREACTORS OR FERMENTERS
- C12M29/00—Means for introduction, extraction or recirculation of materials, e.g. pumps
- C12M29/26—Conditioning fluids entering or exiting the reaction vessel
-
- C—CHEMISTRY; METALLURGY
- C12—BIOCHEMISTRY; BEER; SPIRITS; WINE; VINEGAR; MICROBIOLOGY; ENZYMOLOGY; MUTATION OR GENETIC ENGINEERING
- C12M—APPARATUS FOR ENZYMOLOGY OR MICROBIOLOGY; APPARATUS FOR CULTURING MICROORGANISMS FOR PRODUCING BIOMASS, FOR GROWING CELLS OR FOR OBTAINING FERMENTATION OR METABOLIC PRODUCTS, i.e. BIOREACTORS OR FERMENTERS
- C12M41/00—Means for regulation, monitoring, measurement or control, e.g. flow regulation
- C12M41/30—Means for regulation, monitoring, measurement or control, e.g. flow regulation of concentration
- C12M41/34—Means for regulation, monitoring, measurement or control, e.g. flow regulation of concentration of gas
Landscapes
- Chemical & Material Sciences (AREA)
- Wood Science & Technology (AREA)
- Life Sciences & Earth Sciences (AREA)
- Engineering & Computer Science (AREA)
- Bioinformatics & Cheminformatics (AREA)
- Health & Medical Sciences (AREA)
- Organic Chemistry (AREA)
- Zoology (AREA)
- Biomedical Technology (AREA)
- Sustainable Development (AREA)
- Microbiology (AREA)
- Biochemistry (AREA)
- General Engineering & Computer Science (AREA)
- General Health & Medical Sciences (AREA)
- Genetics & Genomics (AREA)
- Biotechnology (AREA)
- Analytical Chemistry (AREA)
- Apparatus Associated With Microorganisms And Enzymes (AREA)
- Micro-Organisms Or Cultivation Processes Thereof (AREA)
Abstract
Description
【発明の詳細な説明】
〔産業上の利用分野〕
本発明は嫌気性菌の培養方法及び装置に関し、
特に嫌気性菌の液体培養に好適な培養方法及び装
置に関する。[Detailed Description of the Invention] [Industrial Application Field] The present invention relates to a method and apparatus for culturing anaerobic bacteria;
In particular, the present invention relates to a culture method and apparatus suitable for liquid culture of anaerobic bacteria.
従来、有用物質の醗酵生産には好気性菌が用い
られてきた。一方、これまでほとんど利用されて
いなかつた嫌気性菌は好気性菌と生理活性、特に
代謝を異にするため、今後、好気性菌にない有用
物質の生産に利用される可能性が大きい。しか
し、嫌気性菌は分子酸素に弱く、空気中では培養
できず培養前に液体培地中の溶存酸素を除き、さ
らに培養槽気相部の空気を除去する必要がある。
培養はバツチ式で行われるが、従来は培養前に培
地中にチオグリコール酸のアルカリ塩を添加し、
さらに気相部の空気をアルゴン等の高純度不活性
ガスで置換してから培養してきた。
Conventionally, aerobic bacteria have been used for fermentation production of useful substances. On the other hand, anaerobic bacteria, which have been little used until now, have different physiological activities, especially metabolism, from aerobic bacteria, so there is a strong possibility that they will be used in the future to produce useful substances that aerobic bacteria do not have. However, anaerobic bacteria are sensitive to molecular oxygen and cannot be cultured in air, so it is necessary to remove the dissolved oxygen in the liquid medium and the air in the gas phase of the culture tank before culturing.
Cultivation is carried out in batches, but conventionally an alkali salt of thioglycolic acid is added to the medium before culturing.
Furthermore, the air in the gas phase was replaced with a high-purity inert gas such as argon before culturing.
しかし、上記した従来の嫌気性菌培養方法にお
いては、培地中に添加されるチオグリコール酸は
高価であるだけでなく、添加により植菌後の醗酵
開始に要する時間は短縮されるが醗酵速度が低下
し醗酵終了時間が延長する。さらに培養後の培養
濾液や菌体等の有機廃棄物をメタン醗酵処理法に
より廃棄物処理する際、多量の硫化水素ガスが発
生し醗酵の阻害を引き起こす。また、培養槽気相
部のガス置換には、通常培養槽の容積の10倍以上
の高純度不活性ガスを要してきた。
However, in the above-mentioned conventional anaerobic bacterial culture method, thioglycolic acid added to the medium is not only expensive, but also reduces the fermentation rate, although adding it shortens the time required to start fermentation after inoculation. It decreases and the fermentation completion time is extended. Furthermore, when organic wastes such as culture filtrate and bacterial cells are treated by methane fermentation treatment, a large amount of hydrogen sulfide gas is generated, which inhibits fermentation. In addition, gas replacement in the gas phase of a culture tank usually requires high-purity inert gas that is 10 times or more the volume of the culture tank.
本発明の目的は、上記した従来の嫌気性菌培養
方法の欠点を改善するものであつて、嫌気性菌
を、脱酸素剤及び不活性ガスを使用することな
く、効率よく培養する方法及びその実施に使用す
る装置を提供することにある。 The purpose of the present invention is to improve the drawbacks of the conventional anaerobic bacteria culture methods described above, and to provide a method for efficiently culturing anaerobic bacteria without using oxygen scavengers or inert gases, and a method thereof. The objective is to provide equipment used for implementation.
発明者らは、新しい脱酸素処理を組み入れた嫌
気性菌の新しい培養プロセスの開発を目指し鋭意
研究を行つた。嫌気性菌をバツチ式で液体培養を
試みた際、誤つて酸素除去をせずそのまま培養を
行つた。その結果、目的の嫌気性菌は増殖せず、
かわりに混入していた好気性菌の細菌が増殖し
た。気相のガス組成をガスクロマトグラフで分析
したところ、酸素濃度が著しく低下している現象
を見出した。さらに同様の培養実験を行い、嫌気
性菌の培養濾液を基質として気相中のガスをチユ
ーブポンプで液中に循環しつつ好気性菌の培養を
行つたところ、酸素濃度は5ppmにまで低下した。
本現象の発見が契機となり嫌気性菌の培養への応
用を検討した結果、本発明に到達した。
The inventors conducted intensive research with the aim of developing a new culture process for anaerobic bacteria that incorporates a new deoxidizing process. When I tried to culture anaerobic bacteria in batches in liquid, I mistakenly continued the culture without removing oxygen. As a result, the target anaerobic bacteria do not proliferate,
Instead, the aerobic bacteria that had been contaminated grew. When the gas composition of the gas phase was analyzed using a gas chromatograph, it was discovered that the oxygen concentration was significantly reduced. Furthermore, in a similar culture experiment, aerobic bacteria were cultured using the culture filtrate of anaerobic bacteria as a substrate while circulating the gas in the gas phase into the liquid using a tube pump, and the oxygen concentration decreased to 5 ppm. .
The discovery of this phenomenon led us to consider its application to the cultivation of anaerobic bacteria, and as a result, we arrived at the present invention.
本発明の特徴は、嫌気性菌の培養液から産生物
質を分離した残りの有機廃棄物を液体培養基とし
て好気性菌を培養し、その際に生成する脱酸素さ
れた空気を嫌気性菌の培養を開始する際のパージ
用不活性ガスとして利用することである。 A feature of the present invention is that aerobic bacteria are cultured using the remaining organic waste after separating the produced substances from the culture solution of anaerobic bacteria as a liquid culture medium, and the deoxygenated air generated at this time is used to cultivate the anaerobic bacteria. It is used as an inert gas for purging when starting the process.
嫌気性菌を培養した培養液は、培養濾液と菌体
に分離され産生物質の分離用の原料として供され
る。この際、通常は分離後の培養濾液もしくは菌
体スラリは廃棄物として全量、メタン醗酵等の従
来の濃厚有機廃棄物処理に適した方法で処理され
る。本発明では、これらの廃棄物の一部を嫌気性
菌の培養の際のパージ用ガス発生のために再利用
される。まず廃棄物を含む液に好気性菌の種菌液
を添加し、空気を通じて培養する。液中を通過し
た空気はミストを除去後、コンプレツサで圧流
し、加圧状態で貯留される。貯留ガスの酸素濃度
が目標酸素濃度よりまだ高い場合には、培養槽へ
の新鮮な空気の流入を停止し、貯留ガスを循環通
気する。嫌気性菌培養前のパージ用ガスとして用
いうる酸素濃度は10ppm以下、好ましくは5ppm
以下であることが望ましい。嫌気性菌の液体培養
は、培養槽中の液体培地に上記の脱酸素処理空気
を通気し、液中の溶存酸素の除去と気相部の空気
を槽外に排除する。通気に用いるガス量は、醗酵
槽の形状、培地の張り込み率、散気系統の構造等
により変化するが、少なくとも槽容積と同容積を
要する。槽内の脱酸素を行つた後、嫌気性菌の種
菌液を接種し、温度、PH、培地組成、撹拌速度等
の培養条件は使用菌の種類により適宜選定され
る。 A culture solution obtained by culturing anaerobic bacteria is separated into a culture filtrate and bacterial cells, and is used as a raw material for separating produced substances. At this time, the entire culture filtrate or bacterial cell slurry after separation is usually treated as waste by a method suitable for conventional concentrated organic waste treatment such as methane fermentation. In the present invention, a portion of these wastes is reused to generate purge gas during the cultivation of anaerobic bacteria. First, an inoculum of aerobic bacteria is added to a liquid containing waste, and the mixture is cultured through air. After removing the mist from the air that has passed through the liquid, it is forced into a compressor and stored under pressure. If the oxygen concentration of the stored gas is still higher than the target oxygen concentration, the flow of fresh air into the culture tank is stopped and the stored gas is circulated and aerated. The oxygen concentration that can be used as a purge gas before culturing anaerobic bacteria is 10 ppm or less, preferably 5 ppm.
The following is desirable. In liquid culture of anaerobic bacteria, the deoxygenated air described above is aerated into the liquid medium in a culture tank to remove dissolved oxygen in the liquid and expel air in the gas phase to the outside of the tank. The amount of gas used for aeration varies depending on the shape of the fermentation tank, the filling rate of the culture medium, the structure of the aeration system, etc., but it requires at least the same volume as the tank volume. After deoxidizing the tank, an inoculum solution of anaerobic bacteria is inoculated, and culture conditions such as temperature, pH, medium composition, and stirring speed are appropriately selected depending on the type of bacteria used.
本発明で用いる嫌気性菌の基質は、嫌気性菌の
培養後の工程で排出される有機物であれば特に限
定せず、培養濾液や菌体もしくは菌体の粉砕物、
或いは、これら培養濾液や菌体から産生物質を分
離した残りの培養濾液や菌体であつてもよい。好
気性菌としては単一菌を用いてもよいが、二種以
上の混合菌を用いてもよい。この好気性菌として
は、いずれの菌でもよいが、例えばバチルス・ズ
ブチルス、大腸菌等の細菌、サツカロミセス・セ
レビシエ等の酵母、活性汚泥等の混合菌が用いら
れる。培養温度やPHは使用する好気性菌の増殖に
適した条件が選定される。嫌気性菌としては、特
に限定されるものではなく、クロスツリデイウム
属、ビイフイドバクテリウム属等の偏性嫌気性菌
にも十分適用できる。 The substrate for the anaerobic bacteria used in the present invention is not particularly limited as long as it is an organic substance discharged in the process after culturing the anaerobic bacteria, and may include culture filtrate, bacterial cells or crushed bacterial cells,
Alternatively, it may be the remaining culture filtrate or bacterial cells from which produced substances have been separated. As the aerobic bacteria, a single type of bacteria may be used, but a mixture of two or more types of bacteria may be used. The aerobic bacteria may be any type of bacteria, but for example, bacteria such as Bacillus subtilis and Escherichia coli, yeasts such as Satucharomyces cerevisiae, and mixed bacteria such as activated sludge are used. The culture temperature and pH are selected to be conditions suitable for the growth of the aerobic bacteria used. The anaerobic bacteria are not particularly limited, and obligate anaerobic bacteria such as Closturidium and Bifidobacterium can also be sufficiently applied.
培養終了後、培養液は産生物質を分離する工程
に移送される。通常は遠心分離器により濾液及び
菌体スラリに分離され、どちらかから産生物質の
抽出分離が行われる。産生物質の抽出分離の際、
副生する有機廃棄物の一部が好気性菌培養の培地
として返送され再利用される。 After the cultivation is completed, the culture solution is transferred to a process for separating produced substances. Usually, it is separated into a filtrate and a bacterial cell slurry using a centrifuge, and the produced substances are extracted and separated from either of them. When extracting and separating produced substances,
A portion of the by-product organic waste is returned and reused as a medium for aerobic bacterial culture.
本発明の嫌気性菌の培養装置の系統図を第1図
に示す。 A system diagram of the anaerobic bacteria culturing apparatus of the present invention is shown in FIG.
好気性培養槽4は、槽底部に散気管を有してお
り、該散気管により酸素含有気体を槽内に通気す
ることにより、好気性菌を培養することができ
る。本培養槽には、温度調節装置、PH調節装置が
付設されており、温度およPH一定下での培養が可
能である。培養槽内で培養する好気性細菌として
は、バチルス属の如き、好気、嫌気を問わず生育
する細菌を用いる。培養に用いる栄養源として
は、後述する嫌気性菌体スラリ30、および培養
濾液28を用い、嫌気性菌体移送配管32、もし
くは培養濾液移送配管33により、好気性培養槽
に供給される。好気性培養は回分培養方式によつ
て行われる。培養の初期は、空気取り入れ口配管
1により空気を取り込みブロワー2により加圧し
たのち、配管3を経て好気性培養槽4に圧入、散
気する。好気性細菌の培養が対数増殖期に入つた
のち、好気性培養槽より排出される排ガスを配管
5によりサイクロン6に導き、ミストを除去す
る。次いで移送配管8を経て濾過器9に導き、排
ガス中の菌体等の固形物やミストを除いたあと、
コンプレツサ11により加圧し、脱酸素空気加圧
貯槽13に貯留する。脱酸素空気加圧貯槽13へ
のガス貯留量が設定量に達するまで、好気性培養
を継続する。設定量まで貯留した時点において、
空気取り入れ口配管1を閉鎖し、脱酸素空気移送
配管14より脱酸素空気加圧貯槽13内に貯留さ
れた脱酸素空気を好気性菌培養槽4に供給する。
脱酸素空気加圧貯槽13内のガス中の酸素濃度を
測定し、酸素濃度が設定値以下になるまで好気性
菌培養槽4及び脱酸素空気加圧槽13の間で、脱
酸素空気を循環させて所定の酸素濃度の脱酸素空
気を得る。 The aerobic culture tank 4 has an aeration tube at the bottom of the tank, and by aerating oxygen-containing gas into the tank through the aeration tube, aerobic bacteria can be cultured. This culture tank is equipped with a temperature control device and a PH control device, making it possible to culture at a constant temperature and pH. As the aerobic bacteria to be cultured in the culture tank, bacteria such as those of the genus Bacillus, which grow either aerobically or anaerobically, are used. The anaerobic microbial cell slurry 30 and culture filtrate 28, which will be described later, are used as nutrients for the culture, and are supplied to the aerobic culture tank via the anaerobic microbial cell transfer piping 32 or the culture filtrate transfer piping 33. Aerobic culture is performed using a batch culture method. At the initial stage of culture, air is taken in through the air intake pipe 1, pressurized by the blower 2, and then pressurized into the aerobic culture tank 4 via the pipe 3 for aeration. After the culture of aerobic bacteria enters the logarithmic growth phase, the exhaust gas discharged from the aerobic culture tank is guided to a cyclone 6 through a pipe 5 to remove mist. Next, the exhaust gas is led to a filter 9 through a transfer pipe 8, and after removing solids such as bacterial bodies and mist from the exhaust gas,
The deoxygenated air is pressurized by a compressor 11 and stored in a pressurized storage tank 13 . Aerobic culture is continued until the amount of gas stored in the deoxygenated air pressurized storage tank 13 reaches the set amount. Once the set amount has been stored,
The air intake pipe 1 is closed, and the deoxygenated air stored in the deoxygenated air pressurized storage tank 13 is supplied to the aerobic bacteria culture tank 4 from the deoxygenated air transfer pipe 14.
The oxygen concentration in the gas in the deoxygenated air pressurized storage tank 13 is measured, and the deoxygenated air is circulated between the aerobic bacteria culture tank 4 and the deoxygenated air pressurized tank 13 until the oxygen concentration falls below the set value. to obtain deoxygenated air with a predetermined oxygen concentration.
嫌気性菌培養槽18は槽底部に散気管を有して
おり、該散気管は無菌処理脱酸素空気移送配管1
7、濾過器16、脱酸素空気移送配管15を経て
脱酸素空気加圧貯槽13に接続されている。ま
た、本培養槽には撹拌装置、温度調節装置、PH自
動調節装置、及び槽内殺菌設備が付設されてお
り、温度及びPH一定条件下での純粋培養が可能で
ある。嫌気性培養を開始するにあたつては、培養
を目的とする細菌に適した組成を有する液体培地
を嫌気性菌培養槽18に入れ、槽内を滅菌処理す
る。滅菌処理方法は特に限定されるものではな
く、通常用いられる高圧蒸気滅菌法を用いれば十
分である。培地組成中に高温に不安定な物質が存
在する場合には、濾過滅菌法を用いてもよい。培
地の滅菌終了後、培地の温度を培養温度に設定す
る。次いで、嫌気性菌培養槽18内に、脱酸素空
気加圧貯槽13に貯留し濾過器16で除菌した脱
酸素空気を通気し、培養槽内の酸素を除去する。
脱酸素空気の通気量は、培地の張り込み率により
変化するが、少なくとも培養槽容積と同容積以上
が望ましい。培養槽内の酸素の除去を行つたの
ち、嫌気性細菌の種菌液を接種し、所定の温度、
PH、撹拌速度において嫌気培養を開始する。培養
が始まり嫌気性細菌が増殖するのに伴い醗酵ガス
を発生する場合、廃ガス21は廃ガス移送配管2
0により槽外に排出される。なお、廃ガス移送配
管より槽内に空気が逆流するのを防止するため、
配管20の途中に逆流防止手段を設けておくこと
が望ましい。嫌気性菌培養が終了した時点におい
て、嫌気性菌培養液は、嫌気性菌培養液移送用ポ
ンプ34により、培養液移送配管22,23を経
て遠心分離機24に導かれ、培養濾液28及び嫌
気性菌体スラリ30に分離される。培養濾液28
は移送配管26により培養濾液貯槽27に、ま
た、嫌気性菌体スラリ30は移送配管29により
嫌気性菌菌体スラリ貯槽31にそれぞれ一旦貯留
される。産生物質が培養濾液中に含まれている場
合は培養濾液を、菌体スラリ中に含まれている場
合は菌体スラリを産生物質抽出分離工程(図示せ
ず)へ移送し、目的生産物を得る。不要となる培
養濾液または菌体スラリは移送配管32または3
3により好気性菌培養槽4に供給され、好気性細
菌の栄養源として用いさられる。また、有用物質
抽出分離工程より副生する有機生廃棄物も好気性
菌培養のための栄養源として利用することができ
る。 The anaerobic bacteria culture tank 18 has an aeration pipe at the bottom of the tank, and the aeration pipe is connected to the aseptic deoxygenated air transfer pipe 1
7, connected to a deoxygenated air pressurized storage tank 13 via a filter 16 and a deoxygenated air transfer pipe 15. In addition, this culture tank is equipped with a stirring device, temperature control device, automatic pH control device, and in-tank sterilization equipment, allowing pure culture under constant temperature and pH conditions. To start anaerobic culture, a liquid medium having a composition suitable for the bacteria to be cultured is placed in the anaerobic bacteria culture tank 18, and the inside of the tank is sterilized. The sterilization method is not particularly limited, and it is sufficient to use a commonly used high-pressure steam sterilization method. If there are substances unstable at high temperatures in the medium composition, sterilization by filtration may be used. After sterilizing the medium, set the temperature of the medium to the culture temperature. Next, deoxygenated air stored in the deoxygenated air pressurized storage tank 13 and sterilized by the filter 16 is vented into the anaerobic bacteria culture tank 18 to remove oxygen in the culture tank.
The amount of ventilation of deoxygenated air varies depending on the filling rate of the culture medium, but it is preferably at least the same volume as the culture tank volume. After removing the oxygen in the culture tank, inoculate the anaerobic bacteria inoculum and maintain the temperature at the specified temperature.
Start the anaerobic culture at pH, stirring speed. When fermentation gas is generated as the culture begins and anaerobic bacteria proliferate, the waste gas 21 is transferred to the waste gas transfer pipe 2.
0, it is discharged outside the tank. In addition, to prevent air from flowing back into the tank from the waste gas transfer piping,
It is desirable to provide a backflow prevention means in the middle of the piping 20. At the time when the anaerobic bacteria culture is completed, the anaerobic bacteria culture liquid is guided to the centrifuge 24 via the culture liquid transfer pipes 22 and 23 by the anaerobic bacteria culture liquid transfer pump 34, and is separated from the culture filtrate 28 and anaerobic bacteria. The bacterial cells are separated into a slurry 30. Culture filtrate 28
is temporarily stored in the culture filtrate storage tank 27 via the transfer piping 26, and the anaerobic bacterial cell slurry 30 is temporarily stored in the anaerobic bacterial cell slurry storage tank 31 via the transfer piping 29. If the produced substance is contained in the culture filtrate, the culture filtrate is transferred, and if it is contained in the bacterial slurry, the bacterial slurry is transferred to a produced substance extraction and separation process (not shown), and the desired product is extracted. obtain. The unnecessary culture filtrate or bacterial cell slurry is transferred to the transfer pipe 32 or 3.
3 is supplied to the aerobic bacteria culture tank 4 and used as a nutrient source for aerobic bacteria. Furthermore, organic waste produced as a by-product from the useful substance extraction and separation process can also be used as a nutrient source for aerobic bacterial culture.
バチルス・ズブチルス、サツカロミセス・セル
ビシエ等の好気性菌を嫌気性菌の培養廃棄物を栄
養源として培養することにより、残留酸素濃度1
×10-4%以下の脱酸素空気が得られ、この脱酸素
空気を用いてクロスシリジウム等の嫌気性菌が効
率よく培養される。そして、その培養物から該嫌
気性菌の産生物質が回収される。更に、嫌気性菌
の培養液又はこれらから産生物質が回収された残
りの培養廃棄物は上記の通り嫌気性菌の栄養源と
して循環的に使用される。この方法及び装置によ
る嫌気性菌の増殖速度は、次の実施例で示す通り
不純なボンベ窒素や脱酸素剤を使用したものに比
べ顕著に大きく、高価な高純度窒素を使用した場
合のそれに相当するものであつた。
By culturing aerobic bacteria such as Bacillus subtilis and Satucharomyces cerevisiae using the culture waste of anaerobic bacteria as a nutrient source, residual oxygen concentration of 1
Deoxygenated air with a concentration of less than ×10 -4 % is obtained, and anaerobic bacteria such as Crosssilidium can be efficiently cultured using this deoxygenated air. Then, substances produced by the anaerobic bacteria are recovered from the culture. Furthermore, the culture fluid of the anaerobic bacteria or the remaining culture waste from which the substances produced therefrom are recovered, are used cyclically as a nutrient source for the anaerobic bacteria, as described above. The growth rate of anaerobic bacteria using this method and device is significantly higher than that using impure cylinder nitrogen or oxygen scavengers, as shown in the following example, and is comparable to that when using expensive high-purity nitrogen. It was something to do.
実施例 1
可溶性でん粉1.5%、リン酸第1カリウム0.7
%、リン酸第2ソーダ0.35%、硫酸マグネシウム
0.001%、ポリペプトン0.5%、酵母抽出物0.5%を
含む合成培地を用い、嫌気条件下、60℃、PH6.0
にて、、クロスツリジウム属細菌RS−0001(微工
研究寄託No.7918)を培養し、培養液を調製した。
この培養液を遠心分離し、培養濾液と菌体スラリ
を調製した。次に上記培養濾液1.5を内容積30
のステンレス培養槽に入れ、これにバシルス・
ズブチリスの培養液750 2′を種菌として接種し、
通気量0.5/min、30℃、PH6.5で好気培養した。
なお、培養槽からの排ガスは、内容積10のサイ
クロン及び0.45μmのフイルタによつてミストや
固形物を除いたあと、コンプレツサによつて10
Kg/cm2まで圧縮し、内容積1m3の加圧タンクに貯
留した。貯留槽の内圧が10Kg/cm2まで達したのち
は、、貯留ガスを培養槽に循環させて、ガス中の
酸素を消費させた。培養開始24時間後の圧縮脱酸
素空気の酸素濃度を測定した結果、2ppmであつ
た。
Example 1 Soluble starch 1.5%, monopotassium phosphate 0.7
%, Sodium Phosphate 0.35%, Magnesium Sulfate
Using a synthetic medium containing 0.001% polypeptone, 0.5% polypeptone, and 0.5% yeast extract, under anaerobic conditions, 60°C, PH6.0.
Clostridium bacterium RS-0001 (Microtechnology Research Deposit No. 7918) was cultured at , and a culture solution was prepared.
This culture solution was centrifuged to prepare a culture filtrate and a bacterial cell slurry. Next, add 1.5 of the above culture filtrate to an internal volume of 30
Bacillus was placed in a stainless steel culture tank.
Inoculate the culture solution 750 2′ of S. subtilis as a seed,
Aerobic culture was performed at 30°C and pH 6.5 with an aeration rate of 0.5/min.
In addition, the exhaust gas from the culture tank is filtered by a cyclone with an internal volume of 10 mm and a 0.45 μm filter, after which mists and solids are removed, and then a compressor is used to reduce the exhaust gas to 10 mm.
It was compressed to kg/cm 2 and stored in a pressurized tank with an internal volume of 1 m 3 . After the internal pressure of the storage tank reached 10 Kg/cm 2 , the stored gas was circulated through the culture tank to consume oxygen in the gas. The oxygen concentration of the compressed deoxygenated air 24 hours after the start of the culture was measured and found to be 2 ppm.
一方、有効容積1.5m3の培養槽に前記の合成培
地1m3を張り込み、スチームを吹き込んで121℃、
20分間の高圧蒸気滅菌を行つた。60℃に放冷後、
培養槽底部の散気槽から除菌フイルタを通した脱
酸素空気9m3を通気した。通気後の気相部の酸素
濃度は4ppmであつた。培地中の溶存酸素濃度は
0.01ppm以下であつた。これに前記クロスツリジ
ウム属細菌RS−0001の種菌液を10接種し、60
℃、PH6.0で嫌気培養した。培養開始後、直ちに
菌体の増殖が始まり、約16時間後に終了した。19
時間培養後、培養液を遠心分離し、培養濾液910
と菌体スラリ90を得た。 On the other hand, 1 m 3 of the synthetic medium described above was placed in a culture tank with an effective volume of 1.5 m 3 , and steam was blown into the culture tank to raise the temperature to 121°C.
Autoclave sterilization was performed for 20 minutes. After cooling to 60℃,
9 m 3 of deoxygenated air passed through a sterilization filter was vented from the aeration tank at the bottom of the culture tank. The oxygen concentration in the gas phase after ventilation was 4 ppm. The dissolved oxygen concentration in the medium is
It was below 0.01ppm. This was inoculated with 10 inoculum of the Clostridia bacterium RS-0001, and 60
The cells were cultured anaerobically at ℃ and pH 6.0. After the start of the culture, bacterial cell proliferation started immediately and ended after about 16 hours. 19
After incubation for an hour, the culture solution was centrifuged, and the culture filtrate was
A bacterial slurry of 90% was obtained.
比較例 1
有効容積 1.5m3の培養槽に可溶性でん粉1.5
%、リン酸第1カリウム0.7%、リン酸第2ソー
ダ0.35%、硫酸マグネシウム0.001%、ポリペプ
トン0.5%、酵母抽出物0.5%を含む合成培地1m3
を張り込み、スチームを吹き込んで121℃、20分
間の高圧蒸気滅菌を行つた。60℃に放冷後、培養
槽底部の散気管から除菌フイルタを通した窒素
(酸素濃度300ppm)9m3を通気した。通気後の気
相部の酸素濃度は327ppmであつた。また、培地
中の溶存酸素濃度は0.15ppmであつた。これにク
ロスツリジウム属細菌RS−0001の種菌液を10
接種し、60℃、PH6.0で嫌気培養した。その際の
菌体増殖の時間経過を第2図に示した。培養開始
後、約10時間の増殖誘導期ののち増殖が始まり、
22時間後、菌濃度3.0g/まで増殖して終了した。
24時間培養後、培養液を遠心分離し、培養濾液
950と菌体スラリ50を得た。Comparative example 1 Soluble starch 1.5 in a culture tank with an effective volume of 1.5 m3
%, potassium phosphate 0.7%, sodium phosphate 0.35%, magnesium sulfate 0.001%, polypeptone 0.5%, yeast extract 0.5% 1 m 3 of synthetic medium
The container was then sterilized using high-pressure steam at 121°C for 20 minutes by blowing steam into the container. After cooling to 60° C., 9 m 3 of nitrogen (oxygen concentration 300 ppm) passed through a sterilization filter was aerated through the aeration tube at the bottom of the culture tank. The oxygen concentration in the gas phase after ventilation was 327 ppm. Furthermore, the dissolved oxygen concentration in the medium was 0.15 ppm. Add 10 inoculum of Clostridium bacteria RS-0001 to this.
It was inoculated and cultured anaerobically at 60°C and pH 6.0. Figure 2 shows the time course of bacterial cell proliferation at that time. After the start of culture, proliferation begins after a proliferation induction period of about 10 hours.
After 22 hours, the bacteria had grown to a concentration of 3.0 g/min.
After 24 hours of culture, centrifuge the culture solution and collect the culture filtrate.
950 and bacterial cell slurry 50 were obtained.
比較例 2
有効容積1.5m3の培養槽に可溶性でん粉1.5%、
リン酸第1カリウム0.7%、リン酸第2ソーダ
0.35%、硫酸マグネシウム0.001%、ポリペプト
ン0.5%、酵母抽出物0.5%を含む合成培地1m3を
張り込み、スチームを吹き込んで121℃、20分間
の高圧蒸気滅菌を行つた。60℃に放冷後、培養槽
底部の散気管から除菌フイルタを通した窒素(酸
素濃度300ppm)30m3を通気した。通気後の気相
部の酸素濃度は310ppmであつた。培地中の溶存
酸素濃度は0.10ppmであつた。これに前記クロス
ツリジウム属細菌RS−0001の種菌液を10接種
し、60℃、PH6.0で嫌気培養した。その際の菌体
増殖の時間経過を第2図に示した。培養開始後、
菌の増殖が始まるまでに9時間を要し、21時間
後、菌体濃度3.0g/まで増殖して終了した、24
時間培養後。培養液を遠心分離し、培養濾液930
と菌体スラリ70を得た。Comparative Example 2 Soluble starch 1.5% in a culture tank with an effective volume of 1.5 m3 .
Potassium phosphate 0.7%, sodium phosphate dibasic
1 m 3 of a synthetic medium containing 0.35% magnesium sulfate, 0.001% magnesium sulfate, 0.5% polypeptone, and 0.5% yeast extract was poured into the tube, and steam was blown into the tube to perform high-pressure steam sterilization at 121° C. for 20 minutes. After cooling to 60°C, 30 m 3 of nitrogen (oxygen concentration 300 ppm) passed through a sterilization filter was aerated through the aeration pipe at the bottom of the culture tank. The oxygen concentration in the gas phase after ventilation was 310 ppm. The dissolved oxygen concentration in the medium was 0.10 ppm. This was inoculated with 10 inoculum solutions of Clostridium bacteria RS-0001 and cultured anaerobically at 60°C and pH 6.0. Figure 2 shows the time course of bacterial cell proliferation at that time. After starting culture,
It took 9 hours for the bacteria to start growing, and after 21 hours, the bacteria reached a concentration of 3.0g/24.
After incubation for an hour. Centrifuge the culture solution and collect the culture filtrate 930
and a bacterial cell slurry of 70% was obtained.
比較例 3
有効容積1.5m3の培養槽に可溶性でん粉1.5%、
リン酸第1カリウム0.7%、リン酸第2ソーダ
0.35%、硫酸マグネシウム0.001%、ポリペプト
ン0.5%、酵母抽出物0.5%、チオグリコール酸ソ
ーダ0.3%を含む合成培地1m3を張り込み、スチ
ームを吹き込んで121℃、20分間の高圧蒸気滅菌
を行つた。60℃に放冷後、培養槽底部の散気管ら
除菌フイルタを通した窒素(酸素濃度1ppm)9
m3を通気した。通気後の気相部の酸素濃度は
280ppmであつた。培地中の溶存酸素濃度は
0.1ppmであつた。これに前記クロスツリジウム
属細菌RS−0001の種菌液を10接種し、60℃、
PH6.0で嫌気培養した。その際の菌体増殖の時間
経過を第2図に示した。培養開始後、菌が増殖し
はじめるまで11時間を要し、28時間後に菌濃度
2.3g/まで増殖して終了した。30時間培養後、
培養液を遠心分離し、培養濾液960と菌体スラ
リ40を得た。Comparative Example 3 Soluble starch 1.5% in a culture tank with an effective volume of 1.5 m3 .
Potassium phosphate 0.7%, sodium phosphate dibasic
0.35% magnesium sulfate, 0.001% magnesium sulfate, 0.5% polypeptone, 0.5% yeast extract, and 0.3 % sodium thioglycolate. After cooling to 60℃, add nitrogen (oxygen concentration 1 ppm) through a sterilization filter from the aeration pipe at the bottom of the culture tank9
m 3 was vented. The oxygen concentration in the gas phase after ventilation is
It was 280ppm. The dissolved oxygen concentration in the medium is
It was 0.1 ppm. This was inoculated with 10 inoculum of the Clostridia bacterium RS-0001, and incubated at 60°C.
Anaerobic culture was performed at pH 6.0. Figure 2 shows the time course of bacterial cell proliferation at that time. After the start of culture, it takes 11 hours for the bacteria to begin to grow, and after 28 hours the bacterial concentration
The growth was completed to 2.3g/. After 30 hours of culture,
The culture solution was centrifuged to obtain 960 ml of culture filtrate and 40 ml of bacterial cell slurry.
比較例 4
有効容積1.5m3の培養槽に可溶性でん粉1.5%、
リン酸第1カリウム0.7%、リン酸第2ソーダ
0.35%、硫酸マグネシウム0.001%、ポリペプト
ン0.5%、酵母抽出物0.5%を含む合成培地1m3を
張り込み、スチームを吹き込んで121℃、20分間
の高圧蒸気滅菌を行つた。60℃に放冷後、培養槽
底部の散気管から除菌フイルタを通した窒素(酸
素濃度1ppm)9m3を通気した。通気後の気相部
の酸素濃度は3ppmであつた。培地中の溶存酸素
濃度は0.01ppm以下であつた。これに前記クロス
ツリジウム属細菌RS−0001の種菌液を10接種
し、60℃、PH6.0で嫌気培養した。その際の菌体
増殖の時間経過を第2図に示した。培養開始後、
直ちに菌の増殖が始まり、15時間後菌濃度3.5g/
まで増殖したのち終了した。時間培養後、培養
液を遠心分離し、培養濾液905と菌体スラリ95
を得た。Comparative Example 4 Soluble starch 1.5% in a culture tank with an effective volume of 1.5 m3 .
Potassium phosphate 0.7%, sodium phosphate dibasic
1 m 3 of a synthetic medium containing 0.35% magnesium sulfate, 0.001% magnesium sulfate, 0.5% polypeptone, and 0.5% yeast extract was poured into the tube, and steam was blown into the tube to perform high-pressure steam sterilization at 121° C. for 20 minutes. After cooling to 60°C, 9 m 3 of nitrogen (oxygen concentration 1 ppm) passed through a sterilization filter was aerated through the aeration tube at the bottom of the culture tank. The oxygen concentration in the gas phase after ventilation was 3 ppm. The dissolved oxygen concentration in the medium was below 0.01 ppm. This was inoculated with 10 inoculum solutions of Clostridium bacteria RS-0001 and cultured anaerobically at 60°C and pH 6.0. Figure 2 shows the time course of bacterial cell proliferation at that time. After starting culture,
Bacterial growth started immediately, and after 15 hours the bacterial concentration was 3.5g/
It grew until then and then stopped. After culturing for an hour, the culture solution is centrifuged, and the culture filtrate 905 and bacterial cell slurry 95
I got it.
このように、本発明による実施例1では、比較
例1に示す不純なボンベ窒素により酸素置換を行
つた場合や、比較例2のように多量の不純なボン
ベ窒素による置換、及び比較例3の還元剤添加の
場合のいずれと比較しても、増殖速度が大きく、
かつ培養時間の短縮、菌体濃度向上の効果が認め
られる。本実施例と同様の培養効率を得るために
は、比較例4で示されるように、高価な高純度窒
素を多量に用いなければならない。 As described above, in Example 1 according to the present invention, oxygen replacement was performed with impure cylinder nitrogen as shown in Comparative Example 1, replacement with a large amount of impure cylinder nitrogen as in Comparative Example 2, and replacement with a large amount of impure cylinder nitrogen as in Comparative Example 3. The growth rate is higher than in any case where a reducing agent is added.
In addition, the effects of shortening culture time and increasing bacterial cell concentration were observed. In order to obtain the same culture efficiency as in this example, as shown in Comparative Example 4, a large amount of expensive high-purity nitrogen must be used.
実施例 2
可溶性でん粉1.5%、リン酸第1カリウム0.7
%、リン酸第2ソーダ0.35%、硫酸マグネシウム
0.001%、ポリペプトン0.5%、酵母抽出物0.5%を
含む合成培地を用い、嫌気条件下、60℃、PH6.0
にて、クロスツリジウム属細菌RS−0001(微工研
寄託No.7918)を培養し、培養液を調製した。この
培養液を遠心分離し、培養濾液と菌体スラリを調
製した。次に上記培養濾液10を内容積20のス
テンレス培養槽に入れ、これに大腸菌の培養液
500 2′を種菌として接種し、通気量0.5/min、
37℃、PH6.5で好気培養した。なお、培養槽から
の排ガスは、内容積5のサイクロン及び0.45μ
mのフイルタによつてミストや固形物を除いたあ
と、コンプレツサによつて10Kg/cm2まで圧縮し、
内容積1m3の加圧タンクに貯留した。貯留槽の内
圧が10Kg/cm2まで達したのちは、貯留ガスを培養
槽に循環させて、ガス中の酸素を消費させた。培
養開始15時間後の圧縮脱酸素空気の酸素濃度を測
定した結果、3ppmであつた。Example 2 Soluble starch 1.5%, potassium monophosphate 0.7
%, Sodium Phosphate 0.35%, Magnesium Sulfate
Using a synthetic medium containing 0.001% polypeptone, 0.5% polypeptone, and 0.5% yeast extract, under anaerobic conditions, 60°C, PH6.0.
Clostridium bacterium RS-0001 (Feiberal Institute deposited No. 7918) was cultured and a culture solution was prepared. This culture solution was centrifuged to prepare a culture filtrate and a bacterial cell slurry. Next, put the above culture filtrate 10 into a stainless steel culture tank with an internal volume of 20, and add the E. coli culture solution to it.
500 2′ was inoculated as a seed, aeration rate was 0.5/min,
The cells were cultured aerobically at 37°C and pH 6.5. In addition, the exhaust gas from the culture tank is a cyclone with an internal volume of 5 and a 0.45μ
After removing mist and solid matter with a filter, it is compressed to 10Kg/ cm2 using a compressor.
It was stored in a pressurized tank with an internal volume of 1 m 3 . After the internal pressure of the storage tank reached 10 Kg/cm 2 , the stored gas was circulated through the culture tank to consume oxygen in the gas. The oxygen concentration of the compressed deoxygenated air was measured 15 hours after the start of the culture and found to be 3 ppm.
一方、有効容積1.0m3の培養槽に前記の合成培
地0.7m3を張り込み、スチームを吹き込んで121
℃、20分間の高圧蒸気滅菌を行つた。60℃に放冷
後、培養槽底部の散気管から除菌フイルタを通し
た脱酸素空気8m3を通気した。通気後の気相部の
酸素濃度は5ppmであつた。培地中の溶存酸素濃
度は0.01ppm以下であつた。これに前記クロスツ
リジウム属細菌RS−0001の種菌液を7接種し、
60℃、PH6.0で嫌気培養した。その際の菌体増殖
の時間経過を第2図に示した。培養開始後、直ち
に菌の増殖が始まり、14時間後に最大菌濃度3.4
g/に到達して増殖が終了した。18時間培養後、
培養液を遠心分離し、培養濾液630と菌体スラ
リ70を得た。 On the other hand, fill a culture tank with an effective volume of 1.0 m 3 with 0.7 m 3 of the synthetic medium described above, blow steam into it, and
High-pressure steam sterilization was performed at ℃ for 20 minutes. After cooling to 60°C, 8 m 3 of deoxygenated air passed through a sterilization filter was aerated through the aeration tube at the bottom of the culture tank. The oxygen concentration in the gas phase after ventilation was 5 ppm. The dissolved oxygen concentration in the medium was below 0.01 ppm. Seven inoculum solutions of Clostridium bacteria RS-0001 were inoculated into this,
Anaerobic culture was performed at 60°C and pH 6.0. Figure 2 shows the time course of bacterial cell proliferation at that time. Bacterial growth begins immediately after culture begins, and the maximum bacterial concentration reaches 3.4 after 14 hours.
Proliferation was terminated upon reaching g/g/. After 18 hours of incubation,
The culture solution was centrifuged to obtain a culture filtrate 630 and a bacterial cell slurry 70.
実施例 3
可溶性でん粉1.5%、リン酸第1カリウム0.7
%、リン酸第2ソーダ0.35%、硫酸マグネシウム
0.001%、ポリペプトン0.5%、酵母抽出物0.5%を
含む合成培地を用い、嫌気条件下、60℃、PH6.0
にて、クロスツリジウム属細菌RS−0001(微工研
寄託No.7918)を培養し、培養液を調製した。この
培養液を遠心分離し、培養濾液と菌体スラリを調
製し上記培養濾液15を内容積30のステンレス
培養槽に入れ、これにサツカロミセス・シエルビ
シエの培養液750 2′を種菌として接種し、通気量
0.5/min、30℃、PH5.5で好気培養した。なお、
培養槽からの排ガスは、内容積10のサイクロン
及び0.45μmのフイルタによつてミストや固形物
を除いたあと、コンプレツサによつて10Kg/cm2ま
で圧縮し、内容積1m3の加圧タンクに貯留した。
貯留槽の内圧が10Kg/cm2まで達したのちは、貯留
ガスを培養槽に循環させて、ガス中の酸素を消費
させた。培養開始24時間後の圧縮脱酸素空気の酸
素濃度を測定した結果、4ppmであつた。Example 3 Soluble starch 1.5%, potassium phosphate 0.7
%, Sodium Phosphate 0.35%, Magnesium Sulfate
Using a synthetic medium containing 0.001% polypeptone, 0.5% polypeptone, and 0.5% yeast extract, under anaerobic conditions, 60°C, PH6.0.
Clostridium bacterium RS-0001 (Feiberal Institute deposited No. 7918) was cultured and a culture solution was prepared. This culture solution is centrifuged to prepare a culture filtrate and bacterial cell slurry.The above culture filtrate 15 is placed in a stainless steel culture tank with an internal volume of 30, inoculated with culture solution 750 2' of Satucharomyces siervisiae as a seed, and aerated. amount
Aerobic culture was performed at 0.5/min, 30°C, and PH5.5. In addition,
After removing mist and solid matter from the exhaust gas from the culture tank using a cyclone with an internal volume of 10 and a 0.45 μm filter, it is compressed to 10 kg/cm 2 by a compressor and then transferred to a pressurized tank with an internal volume of 1 m 3 . I stored it.
After the internal pressure of the storage tank reached 10 Kg/cm 2 , the stored gas was circulated through the culture tank to consume oxygen in the gas. The oxygen concentration of the compressed deoxygenated air 24 hours after the start of the culture was measured and found to be 4 ppm.
一方、有効容積1.5m3の培養槽に前記の合成培
地1m3を張り込み、スチームを吹き込んで121℃、
20分間の高圧蒸気滅菌を行つた。60℃に放冷後、
培養槽底部の散気管から除菌フイルタを通した脱
酸素空気9m3を通気した。通気後の気相部の酸素
濃度は5ppmであつた。培地中の溶存酸業濃度は
0.01ppm以下であつた。これに前記クロスツリジ
ウム属細菌RS−0001の種菌液を10接種し、60
℃、PH6.0で嫌気培養した。その際の菌体増殖の
時間経過を第2図に示した。培養開始後、直ちに
菌体の増殖が始まり、15時間後に最大菌濃度3.5
g/まで増殖して終了した。18時間培養後、培
養液を遠心分離し、培養濾液908と菌体スラリ
92を得た。 On the other hand, 1 m 3 of the synthetic medium described above was placed in a culture tank with an effective volume of 1.5 m 3 , and steam was blown into the culture tank to raise the temperature to 121°C.
Autoclave sterilization was performed for 20 minutes. After cooling to 60℃,
9 m 3 of deoxygenated air passed through a sterilization filter was vented through the aeration tube at the bottom of the culture tank. The oxygen concentration in the gas phase after ventilation was 5 ppm. The concentration of dissolved acid in the medium is
It was below 0.01ppm. This was inoculated with 10 inoculum of the Clostridia bacterium RS-0001, and 60
The cells were cultured anaerobically at ℃ and pH 6.0. Figure 2 shows the time course of bacterial cell proliferation at that time. After the start of culture, bacterial cells begin to proliferate immediately, reaching a maximum bacterial concentration of 3.5 after 15 hours.
The cells grew to 1.9 g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/sg/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/. After culturing for 18 hours, the culture solution was centrifuged, and the culture filtrate 908 and bacterial cell slurry were separated.
Got 92.
実施例 4
可溶性でん粉1.5%、リン酸第1カリウム0.7
%、リン酸第2ソーダ0.35%、硫酸マグネシウム
0.001%、ポリペプトン0.5%、酵母抽出物0.5%を
含む合成培地を用い、嫌気条件下、60℃、PH6.0
にて、クロスツリジウム属細菌RS−0001(微工研
寄託No.7918)を培養し、培養液を調製した。この
培養液を遠心分離し、培養濾液と菌体スラリを調
製した。次に上記培養濾液10を内容積30のス
テンレス培養槽に入れ、これに活性汚泥10を種
菌として接種し、通気量1.0/min、25℃、PH6.5
で好気培養した。なお、培養槽からの排ガスは、
内容積10のサイクロン及び0.45μmのフイルタ
によつてミストや固形物を除いたあと、コンプレ
ツサによつて10Kg/cm2まで圧縮し、内容積1m3の
加圧タンクに貯留した。貯留槽の内圧が10Kg/cm2
まで達したのちは、貯留ガスを培養槽に循環させ
て、ガス中の酸素を消費させた。培養開始24時間
後の圧縮脱酸素空気の酸素濃度を測定した結果、
6ppmであつた。Example 4 Soluble starch 1.5%, monopotassium phosphate 0.7
%, Sodium Phosphate 0.35%, Magnesium Sulfate
Using a synthetic medium containing 0.001% polypeptone, 0.5% polypeptone, and 0.5% yeast extract, under anaerobic conditions, 60°C, PH6.0.
Clostridium bacterium RS-0001 (Feiberal Institute deposited No. 7918) was cultured and a culture solution was prepared. This culture solution was centrifuged to prepare a culture filtrate and a bacterial cell slurry. Next, the above culture filtrate 10 was placed in a stainless steel culture tank with an internal volume of 30, and activated sludge 10 was inoculated as a seed culture at an air flow rate of 1.0/min, 25°C, and pH 6.5.
Cultured aerobically. In addition, the exhaust gas from the culture tank is
After removing mist and solid matter using a cyclone with an internal volume of 10 and a 0.45 μm filter, it was compressed to 10 Kg/cm 2 using a compressor and stored in a pressurized tank with an internal volume of 1 m 3 . The internal pressure of the storage tank is 10Kg/cm 2
After reaching this point, the stored gas was circulated through the culture tank to consume the oxygen in the gas. As a result of measuring the oxygen concentration of compressed deoxygenated air 24 hours after the start of culture,
It was 6ppm.
一方、有効容積1.5m3の培養槽に前記の合成培
地1m3を張り込み、スチームを吹き込んで121℃、
20分間の高圧蒸気滅菌を行つた。60℃に放冷後、
培養槽底部の散気管から除菌フイルタを通した脱
酸素空気9m3を通気した。通気後の気相部の酸素
濃度は7ppmであつた。培地中の容存酸素濃度は
0.01ppm以下であつた。これに前記クロスツリジ
ウム属細菌RS−0001の種菌液を10接種し、60
℃、PH6.0で嫌気培養した。その際の菌体増殖の
時間経過を第2図に示した。培養開始後、直ちに
菌体の増殖が始まり、15時間後に最大菌濃度3.5
g/まで増殖して培養が終了した。15時間培養
後、培養液を遠心分離し、培養濾液920と菌体
スラリ30を得た。 On the other hand, 1 m 3 of the synthetic medium described above was placed in a culture tank with an effective volume of 1.5 m 3 , and steam was blown into the culture tank to raise the temperature to 121°C.
Autoclave sterilization was performed for 20 minutes. After cooling to 60℃,
9 m 3 of deoxygenated air passed through a sterilization filter was vented through the aeration tube at the bottom of the culture tank. The oxygen concentration in the gas phase after ventilation was 7 ppm. The oxygen concentration in the medium is
It was below 0.01ppm. This was inoculated with 10 inoculum of the Clostridia bacterium RS-0001, and 60
The cells were cultured anaerobically at ℃ and pH 6.0. Figure 2 shows the time course of bacterial cell proliferation at that time. After the start of culture, bacterial cells begin to proliferate immediately, reaching a maximum bacterial concentration of 3.5 after 15 hours.
The culture was completed when the cells proliferated to 1.5 g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/g/; After culturing for 15 hours, the culture solution was centrifuged to obtain culture filtrate 920 and bacterial cell slurry 30.
実施例 5
可溶性でん粉1.5%、リン酸第1カリウム0.7
%、リン酸第2ソーダ0.35%、硫酸マグネシウム
0.001%、ポリペプトン0.5%、酵母抽出物0.5%を
含む合成培地を用い、嫌気条件下、60℃、PH6.0
にて、クロスツリジウム属細菌RS−0001(微工研
寄託No.7918)を培養し、培養液を調製した。この
培養液を遠心分離し、培養濾液と菌体スラリを調
製した。次に上記培養濾液10及び菌体スラリ5
を内容積30のステンレス培養槽に入れ、これ
にバシルス・ズブチリスの培養液750 2′を種菌と
して接種し、通気量0.5/min、30℃、PH6.5で好
気培養した。なお、培養槽からの排ガスは、内容
積10のサイクロン及び0.45μmのフイルタによ
つてミストや固形物を除いたあと、コンプレツサ
によつて10Kg/cm2まで圧縮し、内容積1m3の加圧
タンクに貯留した。貯留槽の内圧が10Kg/cm2まで
達したのちは、、貯留ガスを培養槽に循環させて、
ガス中の酸素を消費させた。培養開始24時間後の
圧縮脱酸素空気の酸素濃度を測定した結果、
1ppmであつた。Example 5 Soluble starch 1.5%, potassium phosphate 0.7
%, Sodium Phosphate 0.35%, Magnesium Sulfate
Using a synthetic medium containing 0.001% polypeptone, 0.5% polypeptone, and 0.5% yeast extract, under anaerobic conditions, 60°C, PH6.0.
Clostridium bacterium RS-0001 (Feiberal Institute deposited No. 7918) was cultured and a culture solution was prepared. This culture solution was centrifuged to prepare a culture filtrate and a bacterial cell slurry. Next, the above culture filtrate 10 and bacterial cell slurry 5
was placed in a stainless steel culture tank with an internal volume of 30 mm, inoculated with culture solution 750 2' of Bacillus subtilis as a seed, and aerobically cultured at 30° C. and pH 6.5 at an air flow rate of 0.5/min. The exhaust gas from the culture tank is used to remove mist and solid matter using a cyclone with an internal volume of 10 and a 0.45 μm filter, and then compressed to 10 Kg/cm 2 by a compressor and then pressurized with an internal volume of 1 m 3 . stored in a tank. After the internal pressure of the storage tank reaches 10Kg/ cm2 , the stored gas is circulated through the culture tank.
The oxygen in the gas was consumed. As a result of measuring the oxygen concentration of compressed deoxygenated air 24 hours after the start of culture,
It was 1ppm.
一方、有効容積1.5m3の培養槽に前記の合成培
地1m3を張り込み、スチームを吹き込んで121℃、
20分間の高圧蒸気滅菌を行つた。60℃に放冷後、
培養槽底部の散気管から除菌フイルタを通した脱
酸素空気9m3を通気した。通気後の気相部の酸素
濃度は3ppmであつた。培地中の溶存酸素濃度は
0.01ppm以下であつた。これに前記クロスツリジ
ウム属細菌RS−0001の種菌液を10接種し、60
℃、PH6.0で嫌気培養した。その際の菌体増殖の
時間経過を第2図に示した。培養開始と同時に菌
の増殖が始まり、14時間後に最大菌濃度3.6g/
まで増殖して培養が終了した。17時間培養後、培
養液を遠心分離し、培養濾液940と菌体スラリ
60を得た。 On the other hand, 1 m 3 of the synthetic medium described above was placed in a culture tank with an effective volume of 1.5 m 3 , and steam was blown into the culture tank to raise the temperature to 121°C.
Autoclave sterilization was performed for 20 minutes. After cooling to 60℃,
9 m 3 of deoxygenated air passed through a sterilization filter was vented through the aeration tube at the bottom of the culture tank. The oxygen concentration in the gas phase after ventilation was 3 ppm. The dissolved oxygen concentration in the medium is
It was below 0.01ppm. This was inoculated with 10 inoculum of the Clostridia bacterium RS-0001, and 60
The cells were cultured anaerobically at ℃ and pH 6.0. Figure 2 shows the time course of bacterial cell proliferation at that time. Bacterial growth begins at the same time as culture begins, and the maximum bacterial concentration reaches 3.6 g/14 hours later.
The culture was completed when the cells proliferated until the end of the culture. After culturing for 17 hours, the culture solution was centrifuged and the culture filtrate 940 and bacterial cell slurry were separated.
Got 60.
本発明によれば、高価であつて、しかも増殖阻
害作用のある還元剤の添加や、多量の高純度不活
性ガスを使用せずに嫌気性菌を短時間で高濃度に
培養することができる。
According to the present invention, anaerobic bacteria can be cultured at a high concentration in a short time without adding an expensive reducing agent that inhibits growth or using a large amount of high-purity inert gas. .
第1図は発明の嫌気性菌の培養装置の系統ずを
示し、第2図は本発明による嫌気性菌培養の菌体
増殖の時間的経過を示す。
1…空気取り入れ口配管、2…ブロアー、3…
空気及び脱酸素空気移送配管、4…好気性菌培養
槽、5…脱酸素空気移送配管、6…サイクロン、
7…好気性菌培養液、8…脱酸素空気移送配管、
9…濾過器、10…脱酸素空気移送配管、11…
コンプレツサ、12…脱酸素空気移送配管、13
…脱酸素空気加圧貯槽、14…脱酸素空気移送配
管、15…脱酸素空気移送配管、16…濾過器、
17…無菌処理脱酸素空気移送配管、18…嫌気
性菌培養槽、19…嫌気性菌培養液、20…廃ガ
ス移送配管、21…廃ガス、22…嫌気性菌培養
液移送配管、23…嫌気性菌培養液移送配管、2
4…遠心分離機、25…回収液移送配管、26…
培養濾液移送配管、27…培養濾液貯槽、28…
培養濾液、29…嫌気性菌菌体スラリ移送配管、
30…嫌気性菌菌体スラリ、31…嫌気性菌菌体
スラリ貯槽、32…嫌気性菌菌体スラリ移送配
管、33…培養濾液移送配管、34…嫌気性菌培
養移送用ポンプ、A…実施例1記載の培養カー
ブ、B…実施例2記載の培養カーブ、C…実施例
3記載の培養カーブ、D…実施例4記載の培養カ
ーブ、E…実施例5記載の培養カーブ、F…比較
例1記載の培養カーブ、G…比較例2記載の培養
カーブ、H…比較例3記載の培養カーブ、I…比
較例4記載の培養カーブ。
FIG. 1 shows the system of the anaerobic bacteria culturing apparatus of the invention, and FIG. 2 shows the time course of cell growth in the anaerobic bacteria culture according to the invention. 1...Air intake piping, 2...Blower, 3...
Air and deoxygenated air transfer piping, 4...Aerobic bacteria culture tank, 5...Deoxygenated air transfer piping, 6...Cyclone,
7...Aerobic bacteria culture solution, 8...Deoxygenated air transfer piping,
9... Filter, 10... Deoxygenated air transfer piping, 11...
Compressor, 12...Deoxygenated air transfer piping, 13
...Deoxygenated air pressurized storage tank, 14...Deoxygenated air transfer piping, 15...Deoxidized air transfer piping, 16...Filter,
17... Aseptic processing deoxygenated air transfer piping, 18... Anaerobic bacteria culture tank, 19... Anaerobic bacteria culture solution, 20... Waste gas transfer piping, 21... Waste gas, 22... Anaerobic bacteria culture solution transfer piping, 23... Anaerobic bacteria culture solution transfer piping, 2
4...Centrifugal separator, 25...Recovered liquid transfer piping, 26...
Culture filtrate transfer piping, 27... Culture filtrate storage tank, 28...
Culture filtrate, 29...anaerobic bacterial cell slurry transfer piping,
30... Anaerobic bacterial cell slurry, 31... Anaerobic bacterial cell slurry storage tank, 32... Anaerobic bacterial cell slurry transfer piping, 33... Culture filtrate transfer piping, 34... Pump for anaerobic bacterial culture transfer, A... Implementation Culture curve described in Example 1, B... Culture curve described in Example 2, C... Culture curve described in Example 3, D... Culture curve described in Example 4, E... Culture curve described in Example 5, F... Comparison Culture curve according to Example 1, G: Culture curve according to Comparative Example 2, H: Culture curve according to Comparative Example 3, I: Culture curve according to Comparative Example 4.
Claims (1)
下に循環的に繰り返し接触させ、該接触により得
られる脱酸素空気を液体培地に通気し、該液体培
地で嫌気性菌を培養することを特徴とする嫌気性
菌の培養方法。 2 脱酸素空気の残留酸素濃度を1×10-4%(V/
V)以下とすることを特徴とする特許請求の範囲
第1項記載の嫌気性菌の培養方法。 3 好気性菌として単一菌又は混合菌を使用する
ことを特徴とする特許請求の範囲第1項記載の嫌
気性菌の培養方法。 4 有機廃棄物が嫌気性菌の培養により生成する
培養濾液あるいは菌体もしくはそれらから産生物
質を除去した培養濾液又は菌体の一種またはそれ
以上の混合物であることを特徴とする特許請求の
範囲第1項記載の嫌気性菌の培養方法。 5 嫌気性菌の培養により生成する有機廃棄物を
含む液と空気を嫌気性菌の存在下で接触させる好
気性菌培養槽と、該培養槽で液と接触した空気を
回収し、繰り返し液と接触させるための脱酸素空
気移送管と、好気性菌培養槽で得られる脱酸素処
理空気を加圧下で貯留する貯留槽と、貯留槽で得
られる貯留脱酸素処理空気を液体培地の入つた培
養槽に通気する脱酸素空気移送管と、脱酸素空気
を通気した液体培地に嫌気性菌を接種し嫌気条件
下で培養する嫌気性菌培養槽と、該培養槽で得ら
れる培養液から嫌気性菌培養に於ける産生物質を
含む培養濾液及び菌体スラリを分離回収する遠心
分離器と、該遠心分離器で得られた培養濾液ある
いは菌体もしくはそれらから産生物質を回収した
残りの培養濾液又は菌体の1種又はそれ以上の混
合物から成る有機廃棄物を好気性菌培養用の基質
として好気性菌培養槽に返送する嫌気性菌培養濾
液又は菌体スラリ移送管とを組合せてなることを
特徴とする嫌気性菌の培養装置。[Claims] 1. Air is repeatedly brought into contact with a liquid containing organic waste in the presence of aerobic bacteria, deoxygenated air obtained by the contact is aerated into a liquid medium, and the liquid medium is anaerobic. A method for culturing anaerobic bacteria characterized by culturing sexual bacteria. 2 Reduce the residual oxygen concentration of deoxygenated air to 1×10 -4 % (V/
V) The method for culturing anaerobic bacteria according to claim 1, which is characterized by the following. 3. The method for culturing anaerobic bacteria according to claim 1, characterized in that a single bacterium or a mixed bacterium is used as the aerobic bacterium. 4. Claim No. 4, characterized in that the organic waste is a culture filtrate or bacterial cells produced by culturing anaerobic bacteria, a culture filtrate from which produced substances have been removed, or a mixture of one or more types of bacterial cells. The method for culturing anaerobic bacteria according to item 1. 5 An aerobic bacteria culture tank in which a liquid containing organic waste generated by culturing anaerobic bacteria is brought into contact with air in the presence of anaerobic bacteria, and the air that has come into contact with the liquid in the culture tank is collected and repeatedly combined with the liquid. A deoxygenated air transfer pipe for contact, a storage tank for storing the deoxygenated air obtained in the aerobic bacteria culture tank under pressure, and a culture medium containing the stored deoxygenated air obtained in the storage tank. A deoxygenated air transfer pipe that ventilates the tank, an anaerobic bacteria culture tank that inoculates anaerobic bacteria into a liquid medium through which deoxygenated air is aerated, and cultivates it under anaerobic conditions; A centrifugal separator that separates and collects the culture filtrate and bacterial cell slurry containing the produced substances in bacterial culture, and the culture filtrate obtained by the centrifugal separator or the remaining culture filtrate from which the bacterial cells or produced substances are recovered. It is combined with an anaerobic bacterial culture filtrate or bacterial slurry transfer tube that returns organic waste consisting of one or more types of bacterial cells to the aerobic bacterial culture tank as a substrate for aerobic bacterial culture. Characteristic anaerobic bacteria culturing device.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP12821886A JPS62285775A (en) | 1986-06-04 | 1986-06-04 | Culture of anaerobe and apparatus therefor |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP12821886A JPS62285775A (en) | 1986-06-04 | 1986-06-04 | Culture of anaerobe and apparatus therefor |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPS62285775A JPS62285775A (en) | 1987-12-11 |
| JPH0522506B2 true JPH0522506B2 (en) | 1993-03-29 |
Family
ID=14979414
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP12821886A Granted JPS62285775A (en) | 1986-06-04 | 1986-06-04 | Culture of anaerobe and apparatus therefor |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPS62285775A (en) |
Families Citing this family (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPH0695928B2 (en) * | 1989-09-29 | 1994-11-30 | 株式会社島津製作所 | Gas chromatograph for microbial culture |
| JP4526712B2 (en) * | 1999-04-23 | 2010-08-18 | 有限会社筑波バイオシステム | Method for culturing basidiomycetes in liquid medium |
-
1986
- 1986-06-04 JP JP12821886A patent/JPS62285775A/en active Granted
Also Published As
| Publication number | Publication date |
|---|---|
| JPS62285775A (en) | 1987-12-11 |
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