JP7446089B2 - Method for producing cellulase - Google Patents
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Description
本発明は、微生物を用いたセルラーゼの製造方法に関する。 The present invention relates to a method for producing cellulase using microorganisms.
糸状菌は、多種のセルラーゼ及びキシラナーゼを生産することから、植物性多糖の分解菌として注目されている。なかでも、トリコデルマ(Trichoderma)は、セルラーゼとキシラナーゼを同時に、かつ大量に生産することが可能であることから、セルラーゼ系バイオマス分解酵素の製造のための微生物として研究されている。 Filamentous fungi are attracting attention as fungi that degrade plant polysaccharides because they produce a wide variety of cellulases and xylanases. Among them, Trichoderma is being researched as a microorganism for producing cellulase-based biomass-degrading enzymes because it can simultaneously produce cellulase and xylanase in large quantities.
微生物の培養においては、従来、炭素源としてグルコースが汎用されている。また、微生物による酵素などタンパク質の生産には、炭素源に加えて、誘導物質が必要なことがある。例えば、アスペルギルス・オリゼのαアミラーゼ遺伝子の発現は、デンプンやマルトースなどに誘導される。 Glucose has conventionally been widely used as a carbon source in the cultivation of microorganisms. Furthermore, in addition to a carbon source, an inducer may be required for the production of proteins such as enzymes by microorganisms. For example, expression of the α-amylase gene of Aspergillus oryzae is induced by starch, maltose, and the like.
特許文献1には、バッチ相における、炭素質生育基質の存在下での菌の生育のための第1の工程と、流加相における、誘導炭素質基質の存在下での菌の生育及び酵素生産のための第2の工程を含む、糸状菌を用いたセルラーゼの生産方法、ならびに、該炭素質生育基質がラクトース、グルコース、キシロース、セルロース系バイオマスの酵素加水分解物の単量体糖のエタノール発酵後に得られる残渣、及びセルロース系バイオマスの前処理に由来する水溶性ペントースの粗抽出物から選択され、該誘導炭素質基質が、ラクトース、セロビオース、ソホロース、セルロース系バイオマスの酵素加水分解物の単量体糖のエタノール発酵後に得られる残渣、及びセルロース系バイオマスの前処理に由来する水溶性ペントースの粗抽出物から選択されることが開示されている。特許文献2には、トリコデルマ等の菌類によってセルロース又はヘミセルロース分解性酵素を生産する方法において、酵素生産のための炭素源及び誘導炭素源としてセルロース性又はリグノ-セルロース性材料の酵素加水分解物のエタノール発酵からの残渣(グルコース、キシロース等を含む)を用いることが開示されている。特許文献3には、流加バッチ又は連続発酵培地において、培地に添加した炭素量と、消費した酸素量又は二酸化炭素へと消失した炭素量とに基づいて、発酵培地に対する炭素添加速度を制御する方法が開示され、また該方法を用いて微生物に酵素などのタンパク質を生産させることが開示されている。トリコデルマの主要なセルラーゼ遺伝子cbh1、cbh2、egl1及びegl2の発現は、セルロース、セロビオースなどにより誘導される(非特許文献1)。 Patent Document 1 describes a first step for bacterial growth in the presence of a carbonaceous growth substrate in a batch phase, and a first step for bacterial growth in the presence of an induced carbonaceous substrate and an enzyme in a fed-batch phase. A method for producing cellulase using filamentous fungi, comprising a second step for production, and the carbonaceous growth substrate is ethanol of monomeric sugars such as lactose, glucose, xylose, and enzymatic hydrolysates of cellulosic biomass. The derivatized carbonaceous substrate is selected from the residue obtained after fermentation and the crude extract of water-soluble pentoses derived from the pretreatment of cellulosic biomass, and the derivatized carbonaceous substrate is a monomer of lactose, cellobiose, sophorose, enzymatic hydrolyzate of cellulosic biomass. and the crude extract of water-soluble pentoses derived from the pretreatment of cellulosic biomass. Patent Document 2 describes a method for producing cellulose- or hemicellulose-degrading enzymes using fungi such as Trichoderma, in which ethanol of an enzymatic hydrolyzate of a cellulosic or ligno-cellulosic material is used as a carbon source and a derived carbon source for enzyme production. The use of residues from fermentation (including glucose, xylose, etc.) is disclosed. Patent Document 3 discloses that in a fed-batch or continuous fermentation medium, the rate of carbon addition to the fermentation medium is controlled based on the amount of carbon added to the medium and the amount of oxygen consumed or the amount of carbon lost to carbon dioxide. A method is disclosed, and the use of the method to cause microorganisms to produce proteins, such as enzymes, is disclosed. The expression of major cellulase genes cbh1, cbh2, egl1, and egl2 of Trichoderma is induced by cellulose, cellobiose, etc. (Non-Patent Document 1).
微生物により安価かつ効率よく酵素等のタンパク質を製造するための培養技術の開発が求められている。グルコース存在下では、カタボライト抑制と呼ばれる制御機構により、微生物による物質生産性の低下又は飽和が起こる。例えばトリコデルマ等の糸状菌でも、カタボライト抑制が報告されており、その機構解析が進められている。グルコースを繰り返し又は継続的に培養物に流加する流加培養により、カタボライト抑制が抑止され、微生物のタンパク質生産性が向上する可能性がある。しかし、グルコース流加培養によるタンパク質生産では、カタボライト抑制を防ぐため、培養物中のグルコース濃度の精密な制御が求められる。 There is a need for the development of culture techniques for producing proteins such as enzymes inexpensively and efficiently using microorganisms. In the presence of glucose, a control mechanism called catabolite suppression causes a decrease or saturation of material productivity by microorganisms. For example, catabolite suppression has been reported in filamentous fungi such as Trichoderma, and the mechanism is being analyzed. Fed-batch culture, in which glucose is repeatedly or continuously fed into the culture, may inhibit catabolite suppression and improve microbial protein productivity. However, protein production by glucose fed-batch culture requires precise control of the glucose concentration in the culture to prevent catabolite suppression.
本発明者らは、微生物を用いたセルラーゼ製造において、セルロース等のセルラーゼ生産を誘導する誘導炭素基質とグルコース等の非誘導炭素基質とを、それらの比率を微生物の呼吸活性の状態に依存して調整しながら培養培地に供給することによって、微生物のセルラーゼ生産性が向上することを見出した。 In the production of cellulase using microorganisms, the present inventors determined the ratio of induced carbon substrates such as cellulose that induce cellulase production and non-induced carbon substrates such as glucose depending on the state of respiratory activity of the microorganisms. It has been found that cellulase productivity of microorganisms can be improved by adjusting the supply to the culture medium.
本発明は、セルラーゼの製造方法であって、
誘導炭素基質及び非誘導炭素基質の存在下で糸状菌を培養することを含み、
該糸状菌の呼吸活性の変化率が0.1以上である期間において、下記式Aで表される比Rが100以下である、
式A:R=非誘導炭素基質の供給速度/誘導炭素基質の供給速度
方法を提供する。
The present invention is a method for producing cellulase, comprising:
culturing the filamentous fungus in the presence of an induced carbon substrate and a non-induced carbon substrate;
During the period when the rate of change in the respiratory activity of the filamentous fungus is 0.1 or more, the ratio R represented by the following formula A is 100 or less,
Formula A: R=Feed Rate of Underivatized Carbon Substrate/Feed Rate of Derived Carbon Substrate Methods are provided.
本発明は、微生物からのセルラーゼの収率を向上させることができる。 The present invention can improve the yield of cellulase from microorganisms.
本発明は、微生物を用いたセルラーゼの製造方法を提供する。本発明によるセルラーゼの製造方法は、誘導炭素基質及び非誘導炭素基質の存在下でセルラーゼ生産性微生物を培養することを含む。 The present invention provides a method for producing cellulase using a microorganism. The method for producing cellulase according to the present invention includes culturing a cellulase-producing microorganism in the presence of an induced carbon substrate and a non-induced carbon substrate.
本発明の方法で培養されるセルラーゼ生産性微生物の例としては、細菌、酵母、糸状菌などが挙げられ、このうち糸状菌が好ましい。糸状菌としては、例えば、Acremonium属、Aspergillus属、Aureobasidium属、Bjerkandera属、Ceriporiopsis属、Chrysosporium属、Coprinus属、Coriolus属、Cryptococcus属、Filibasidium属、Fusarium属、Humicola属、Magnaporthe属、Mucor属、Myceliophthora属、Neocallimastix属、Neurospora属、Paecilomyces属、Penicillium属、Phanerochaete属、Phlebia属、Piromyces属、Pleurotus属、Rhizopus属、Schizophyllum属、Talaromyces属、Thermoascus属、Thielavia属、Tolypocladium属、Trametes属、及びTrichoderma属の糸状菌が挙げられ、このうち、アクレモニウム属(Acremonium)、アスペルギルス属(Aspergillus)、クリソスポリウム属(Chrysosporium)、フサリウム属(Fusarium)、フミコーラ属(Humicola)、ミセリオフトラ属(Myceliophthora)、ニューロスポラ属(Neurospora)、ペニシリウム属(Penicillium)、ピロマイセス属(Piromyces)、タラロマイセス属(Talaromyces)、サーモアスカス属(Thermoascus)、チエラビア属(Thielavia)、及びトリコデルマ属(Trichoderma)が好ましい。セルラーゼの生産性、及び得られたセルラーゼのバイオマス糖化性能の観点からは、トリコデルマ属がより好ましく、トリコデルマ・リーセイ(Trichoderma reesei)及びその変異株がさらに好ましい。トリコデルマ・リーセイ及びその変異株の例としては、トリコデルマ・リーセイQM9414株、PC-3-7株、及びそれらの変異株が挙げられる。該変異株としては、遺伝子の突然変異、遺伝子組換え等の改変により生じた変異株が挙げられる。 Examples of cellulase-producing microorganisms to be cultured in the method of the present invention include bacteria, yeast, filamentous fungi, and among these, filamentous fungi are preferred. Examples of filamentous fungi include Acremonium genus, Aspergillus genus, Aureobasidium genus, Bjerkandera genus, Ceriporiopsis genus, Chrysosporium genus, Coprinus genus, Coriolus genus, Cryptococcus Us, Filibasidium, Fusarium, Humicola, Magnaporthe, Mucor, Myceliophthora Genus, Neocallimastix, Neurospora, Paecilomyces, Penicillium, Phanerochaete, Phlebia, Piromyces, Pleurotus, Rhizopus, Schizophrenia phyllum, Talaromyces, Thermoascus, Thielavia, Tolypocladium, Trametes, and Trichoderma Among these, Acremonium, Aspergillus, Chrysosporium, Fusarium, Humicola, Myceliophthora, and B Neurospora, Penicillium, Piromyces, Talaromyces, Thermoascus, Thielavia, and Trichoderm a) is preferred. From the viewpoint of cellulase productivity and biomass saccharification performance of the obtained cellulase, Trichoderma is more preferred, and Trichoderma reesei and its mutants are even more preferred. Examples of Trichoderma reesei and mutant strains thereof include Trichoderma reesei QM9414 strain, PC-3-7 strain, and mutant strains thereof. Examples of the mutant strain include mutant strains produced by modifications such as gene mutation and genetic recombination.
当該微生物の培養に用いられる誘導炭素基質は、該微生物のセルラーゼ発現を誘導する炭素基質であればよい。該誘導炭素基質の例としては、微生物のセルラーゼ発現を誘導する糖類、例えばラクトース、セロビオース、ソホロース、ゲンチオビオース、及びセルロースからなる群より選択される少なくとも1種が挙げられる。これらの誘導炭素基質は、一般に誘導酵素といわれているセルラーゼを培養生産するために、本発明の方法において必須の炭素基質である。セルラーゼ誘導性及びコストの観点から、好ましくは、該誘導炭素基質はセルロースである。セルロースは、結晶性セルロース、セルロース系バイオマス、又はそれらの粉砕物であってもよい。 The induced carbon substrate used for culturing the microorganism may be any carbon substrate that induces cellulase expression in the microorganism. Examples of the induced carbon substrate include saccharides that induce cellulase expression in microorganisms, such as at least one selected from the group consisting of lactose, cellobiose, sophorose, gentiobiose, and cellulose. These derivatized carbon substrates are essential carbon substrates in the method of the present invention in order to culture and produce cellulase, which is generally referred to as an inducible enzyme. From the viewpoint of cellulase inducibility and cost, preferably the derivatized carbon substrate is cellulose. The cellulose may be crystalline cellulose, cellulosic biomass, or pulverized products thereof.
当該微生物の培養に用いられる非誘導炭素基質は、該微生物のセルラーゼ発現を誘導せず、かつ一般に該微生物のカタボライト抑制(セルラーゼ発現停止)をもたらす炭素基質である。該非誘導炭素基質の例としては、微生物のセルラーゼ発現を誘導しない糖類、例えばグルコース、フルクトース、スクロース、マルトース、及びマルトオリゴ糖からなる群より選択される少なくとも1種が挙げられる。このうち、微生物培養における汎用性及び資化性の観点からは、グルコース、マルトース、及びマルトオリゴ糖からなる群より選択される少なくとも1種が好ましい。 A non-inducing carbon substrate used for culturing the microorganism is a carbon substrate that does not induce cellulase expression in the microorganism and generally results in catabolite suppression (cessation of cellulase expression) in the microorganism. Examples of the non-inducing carbon substrate include sugars that do not induce cellulase expression in microorganisms, such as at least one selected from the group consisting of glucose, fructose, sucrose, maltose, and maltooligosaccharides. Among these, at least one selected from the group consisting of glucose, maltose, and maltooligosaccharides is preferred from the viewpoint of versatility and assimilation in microbial culture.
該誘導炭素基質は、好ましくは培養槽にバッチ添加される。より好ましくは、該誘導炭素基質は初期培地に添加される。培養槽における誘導炭素基質の初期濃度(例えば初期培地における誘導炭素基質の濃度)は、好ましくは1~15質量/容量%である。一方、培養槽への非誘導炭素基質の添加は、微生物のカタボライト抑制を避ける観点からは連続添加(例えば流加)であることが好ましい。より好ましくは、該非誘導炭素基質は培養槽に流加される。例えば、該非誘導炭素基質の水溶液を培養槽に流加すればよい。流加される水溶液中における該非誘導炭素基質の濃度は、好ましくは2~90質量/容量%、より好ましくは5~80質量/容量%である。流加される水溶液中の非誘導炭素基質の濃度が低すぎると、培養物へ大量の水溶液を流加することになるため培養設備に負担がかかる。一方、該水溶液中の非誘導炭素基質の濃度が高すぎると、培養物への非誘導炭素基の流加量の制御が困難になる。 The derivatized carbon substrate is preferably added in batches to the culture vessel. More preferably, the derivatized carbon substrate is added to the initial medium. The initial concentration of the induced carbon substrate in the culture vessel (eg the concentration of the induced carbon substrate in the initial medium) is preferably between 1 and 15% w/v. On the other hand, it is preferable that the non-induced carbon substrate be added to the culture tank continuously (for example, fed-batch) from the viewpoint of avoiding suppression of microbial catabolites. More preferably, the uninduced carbon substrate is fed to the culture tank. For example, an aqueous solution of the non-induced carbon substrate may be added to a culture tank. The concentration of the uninduced carbon substrate in the fed aqueous solution is preferably 2 to 90% by weight/volume, more preferably 5 to 80% by weight/volume. If the concentration of the non-induced carbon substrate in the aqueous solution to be fed is too low, a large amount of the aqueous solution will be fed to the culture, which will place a burden on the culture equipment. On the other hand, if the concentration of the non-induced carbon substrate in the aqueous solution is too high, it becomes difficult to control the amount of non-induced carbon groups added to the culture.
該培養に用いられる誘導炭素基質及び非誘導炭素基質は、滅菌されていることが好ましい。該炭素基質をバッチ添加する場合、初期培地等とともに培養槽に導入された後で滅菌されてもよく、又は予め滅菌された後で培養槽に添加されてもよい。該炭素基質を流加する場合、予め滅菌した後で培養槽に流加すればよい。該炭素基質の滅菌には、一般的には加熱滅菌、高圧蒸気滅菌器(オートクレーブ)による加圧加熱滅菌、飽和水蒸気の吹付けによる滅菌など、が採用され得る。滅菌条件としては、耐熱性菌であるGeobacillus stearothermophilusの芽胞数が10-12倍まで減少する条件(例えば、120℃で20分と同等)もしくはより過酷な条件が挙げられる。 The induced carbon substrate and non-induced carbon substrate used in the culture are preferably sterilized. When adding the carbon substrate in batches, it may be sterilized after being introduced into the culture tank together with the initial medium etc., or it may be sterilized in advance and then added to the culture tank. When feeding the carbon substrate, it may be sterilized in advance and then fed into the culture tank. For sterilization of the carbon substrate, generally heat sterilization, pressure heat sterilization using a high-pressure steam sterilizer (autoclave), sterilization by spraying saturated steam, etc. may be employed. Sterilization conditions include conditions that reduce the number of spores of Geobacillus stearothermophilus, a heat-resistant bacterium, by 10 -12 times (e.g., equivalent to 20 minutes at 120° C.) or harsher conditions.
本発明の方法の一例では、培養槽に、該誘導炭素基質を含有する初期培地を導入し、次いで該培養槽を滅菌する。該滅菌された培養槽に微生物を播種した後、該非誘導炭素基質の水溶液を流加しながら該微生物を培養する。 In one example of the method of the invention, a culture vessel is introduced with an initial medium containing the derivatized carbon substrate, and then the culture vessel is sterilized. After the microorganisms are seeded in the sterilized culture tank, the microorganisms are cultured while being fed with the aqueous solution of the non-induced carbon substrate.
該培養に使用される初期培地は、培養される微生物に通常使用される培地であればよい。例えば、該初期培地は、上記誘導炭素基質を含む炭素源、窒素源、マグネシウム塩、亜鉛塩等の金属塩、硫酸塩、リン酸塩、pH調整剤、界面活性剤、消泡剤などの微生物の培地に一般的に含まれる各種成分を含有することができる。培地中の成分組成は適宜選択可能である。該初期培地は、合成培地、天然培地、半合成培地のいずれであってもよく、又は市販の培地であってもよい。該初期培地は、好ましくは液体培地である。 The initial medium used for the culture may be any medium commonly used for the microorganism to be cultured. For example, the initial medium may contain microorganisms such as a carbon source including the above-mentioned induced carbon substrate, a nitrogen source, metal salts such as magnesium salts and zinc salts, sulfates, phosphates, pH adjusters, surfactants, and antifoaming agents. It can contain various components commonly included in culture media. The component composition in the medium can be selected as appropriate. The initial medium may be a synthetic medium, a natural medium, a semi-synthetic medium, or a commercially available medium. The initial medium is preferably a liquid medium.
培養槽への非誘導炭素基質の流加は、通常の流加培養の手順に従って実施され得る。例えば、一般的なフィードコントローラなどを用いて流加量を制御しながら、非誘導炭素基質の水溶液を培養槽に流加すればよい。培養槽への非誘導炭素基質の流加は、培養開始とともに開始してもよく、又は後述する微生物の呼吸活性の変化率が一定値(例えば0.1以上)に達したのちに開始してもよい。培養開始とともに非誘導炭素基質の流加を開始すると簡便である。非誘導炭素基質の流加速度の初期値は、炭素濃度換算で、0.15~0.50g/L-初期培地/hが好ましいが、誘導炭素基質濃度や菌体濃度に依存して調整可能である。 Feeding the non-induced carbon substrate to the culture vessel may be carried out according to conventional fed-batch culture procedures. For example, an aqueous solution of a non-induced carbon substrate may be added to the culture tank while controlling the amount of addition using a general feed controller or the like. The addition of the non-inducing carbon substrate to the culture tank may be started at the same time as the start of the culture, or after the rate of change in the respiration activity of the microorganisms described below reaches a certain value (for example, 0.1 or more). Good too. It is convenient to start feeding the non-induced carbon substrate at the same time as the start of culture. The initial value of the flow rate of the non-induced carbon substrate is preferably 0.15 to 0.50 g/L-initial medium/h in terms of carbon concentration, but it can be adjusted depending on the induced carbon substrate concentration and bacterial cell concentration. be.
本発明の方法において、微生物培養中における該誘導炭素基質と該非誘導炭素基質の培養培地に対する供給量は、培養する微生物の呼吸活性の状態に依存して調整される。より詳細には、培養中の微生物の呼吸活性の変化率が0.1以上である期間において、該誘導炭素基質の供給速度に対する該非誘導炭素基質の供給速度の比R〔R=非誘導炭素基質の供給速度/誘導炭素基質の供給速度〕は、100以下、好ましくは50以下、より好ましくは10以下に調整される。他方、誘導炭素基質の消費を節減する観点からは、該誘導炭素基質の供給速度に対する該非誘導炭素基質の供給速度の比は、1以上であることが好ましい。 In the method of the present invention, the amount of the induced carbon substrate and the non-induced carbon substrate supplied to the culture medium during microbial culture is adjusted depending on the state of respiratory activity of the microorganism to be cultured. More specifically, during a period in which the rate of change in the respiratory activity of microorganisms during culture is 0.1 or more, the ratio R of the supply rate of the non-induced carbon substrate to the supply rate of the induced carbon substrate [R = non-induced carbon substrate feed rate of the derivatized carbon substrate] is adjusted to 100 or less, preferably 50 or less, more preferably 10 or less. On the other hand, from the viewpoint of reducing consumption of the induced carbon substrate, the ratio of the supply rate of the non-induced carbon substrate to the rate of supply of the induced carbon substrate is preferably 1 or more.
微生物の代謝制御の観点からは、本発明の方法においては、培養中の該微生物の呼吸活性の変化率が0.1以上である期間に続く、該微生物の呼吸活性の変化率が0.01以上である期間において、上記比Rを100以下、好ましくは50以下、より好ましくは10以下に調整することが好ましい。 From the viewpoint of metabolic control of microorganisms, in the method of the present invention, the rate of change in the respiratory activity of the microorganism during culture is 0.01 or more following a period in which the rate of change in the respiratory activity of the microorganism is 0.01 or more. In the above period, it is preferable to adjust the ratio R to 100 or less, preferably 50 or less, more preferably 10 or less.
微生物の代謝制御の観点からは、本発明の方法においては、培養中該微生物の呼吸活性の変化率が0.01以上である期間に続く、該微生物の呼吸活性の変化率が0.001以上である期間において、上記比Rを100以下、好ましくは50以下、より好ましくは10以下に調整することがさらに好ましい。 From the viewpoint of metabolic control of microorganisms, in the method of the present invention, the rate of change in the respiratory activity of the microorganism is 0.001 or more following a period in which the rate of change in the respiratory activity of the microorganism is 0.01 or more during culture. It is further preferable to adjust the ratio R to 100 or less, preferably 50 or less, and more preferably 10 or less during a certain period.
本明細書において、微生物の呼吸活性は、菌体の呼吸に由来する培養物からのCO2排出速度を、該培養物の菌体濃度で除することで算出される。例えば、微生物の呼吸活性は、下記式(1)に従って算出され得る。またCO2排出速度は、該培養物の単位時間当たりCO2総排出量[g-CO2]から、培養物の容量及び時間当たりのCO2排出量の変化率を求めることによって算出され得る。例えば、培養物の単位時間当たりCO2総排出量[g-CO2]は、培養物のCO2濃度[vol%]と培養通気量に基づいて、下記式(2)に従って算出され得る。
呼吸活性[g-CO2/g-dry cell/h]
=(CO2排出速度[g-CO2/L-培養物/h])÷(菌体濃度[g-dry cell/L-培養物]) …(1)
ここで、
g-CO2 =(CO2濃度[vol%]÷100 × 培養通気量[L/min]×60[min])
÷([モル体積] × 44[CO2モル質量]) …(2)
ここで、CO2濃度[vol%]:培養物中CO2濃度(vol%)
g-dry cell:CO2濃度[vol%]計測時の培養物に含まれる菌体の乾燥質量(g)
L-培養物:CO2濃度[vol%]計測時の培養物量(L)
In this specification, the respiratory activity of a microorganism is calculated by dividing the rate of CO 2 excretion from a culture derived from bacterial respiration by the bacterial cell concentration of the culture. For example, the respiratory activity of a microorganism can be calculated according to the following formula (1). Further, the CO 2 emission rate can be calculated by determining the volume of the culture and the rate of change in the CO 2 emission per unit time from the total CO 2 emission per unit time [g-CO 2 ] of the culture. For example, the total amount of CO 2 discharged per unit time [g-CO 2 ] of the culture can be calculated according to the following formula (2) based on the CO 2 concentration [vol%] of the culture and the amount of culture aeration.
Respiratory activity [g-CO 2 /g-dry cell/h]
= (CO 2 emission rate [g-CO 2 /L-culture/h]) ÷ (bacterial cell concentration [g-dry cell/L-culture]) …(1)
here,
g-CO 2 = (CO 2 concentration [vol%] ÷ 100 × culture aeration rate [L/min] × 60 [min])
÷ ([molar volume] × 44[CO 2 molar mass]) …(2)
Here, CO 2 concentration [vol%]: CO 2 concentration in culture (vol%)
g-dry cell: Dry mass (g) of bacterial cells contained in the culture when measuring CO2 concentration [vol%]
L-Culture: Culture volume (L) when measuring CO2 concentration [vol%]
培養物のCO2濃度[vol%]は、培養槽用の排ガス分析装置により測定することができる。該排気ガス分析装置としては、非分散赤外線吸収方式の排気ガス分析装置(例えばDEX-1562A;株式会社バイオット)などを用いることができるが、これに限定されない。培養物における培養通気量は、流量計(例えば、コフロック株式会社製フローメータ)により測定することができる。例えばバルブ付フローメータ(例えば、コフロック株式会社製)により、通気量を制御しつつ流量を測定することが好ましい。 The CO 2 concentration [vol%] of the culture can be measured using an exhaust gas analyzer for culture tanks. As the exhaust gas analyzer, a non-dispersive infrared absorption type exhaust gas analyzer (for example, DEX-1562A; manufactured by Biot Co., Ltd.) can be used, but the exhaust gas analyzer is not limited thereto. The amount of aeration in the culture can be measured using a flow meter (for example, a flow meter manufactured by Cofloc Co., Ltd.). For example, it is preferable to measure the flow rate while controlling the ventilation amount using a flow meter with a valve (for example, manufactured by COFLOC Co., Ltd.).
本発明の方法において、微生物の呼吸活性は、上記式(1)及び(2)に従って毎時算出され得る。経時的に測定される呼吸活性から、該呼吸活性の変化率を求めることができる。すなわち、呼吸活性の変化率は、下記式(3)のとおり、連続する2つの測定時点で算出された呼吸活性の差分を、より早い時点で算出した呼吸活性で除すことにより算出される。
呼吸活性の変化率 ={|時間t2における呼吸活性 - 時間t1における呼吸活性|
÷(時間t1における呼吸活性)}(t2>t1, |t1-t2| = 1)…(3)
In the method of the present invention, the respiratory activity of microorganisms can be calculated hourly according to equations (1) and (2) above. From the respiratory activity measured over time, the rate of change in the respiratory activity can be determined. That is, the rate of change in respiratory activity is calculated by dividing the difference in respiratory activity calculated at two consecutive measurement points by the respiratory activity calculated at an earlier point in time, as shown in equation (3) below.
Rate of change in respiratory activity = {|Respiratory activity at time t 2 - Respiratory activity at time t 1 |
÷ (respiratory activity at time t 1 )} (t 2 > t 1 , | t 1 − t 2 | = 1)…(3)
本発明において、バッチ添加される場合の誘導炭素基質の供給速度は、培養物中の誘導炭素基質由来の炭素の単位時間当たりの濃度変化(消失速度)として定義される。誘導炭素基質由来の炭素の消失速度は、例えば、以下の手順にて測定することができる:
(1)まず、サンプリングした培養物から遠心分離等で固形分を分取する。これにより培地に溶解する非誘導炭素基質は実質的に除去される。得られた固形分を乾燥させ、乾燥固形分の質量を測定する。次いで、該乾燥固形分を元素分析し、乾燥固形分中の全炭素量を求める。全炭素量から、微生物体由来の炭素量を差し引くことで、誘導炭素基質由来の炭素量を求める。すなわち、培養中の微生物体のC/N比は一定であると仮定して、種菌培養時の微生物体サンプルの測定により算出した菌体のC/N比と、該乾燥固形分中の窒素量から、該乾燥固形分中の微生物体由来の炭素量を算出する。乾燥固形分の全炭素量と微生物体由来の炭素量との差分が、誘導炭素基質由来の炭素量として算出され、これを培養物量で除することで、培養物中の誘導炭素基質由来の炭素濃度が求められる。
(2)次いで異なる2つの時点で算出された誘導炭素基質由来の炭素濃度の差分を求める。該差分値は、培養物中の誘導炭素基質由来の炭素濃度の該2つの時点間での濃度変化を反映する。よって、該差分値から単位時間当たりの濃度変化を算出することで、培養物に対する誘導炭素基質の供給速度[g-誘導炭素基質由来の炭素/L-培養液/h]を決定することができる。
In the present invention, the feed rate of the derivatized carbon substrate when added batchwise is defined as the concentration change per unit time (disappearance rate) of carbon from the derivatized carbon substrate in the culture. The rate of carbon disappearance from the derived carbon substrate can be measured, for example, by the following procedure:
(1) First, the solid content is separated from the sampled culture by centrifugation or the like. This substantially eliminates uninduced carbon substrates that dissolve in the medium. The obtained solid content is dried and the mass of the dry solid content is measured. Next, the dry solid content is subjected to elemental analysis to determine the total carbon content in the dry solid content. The amount of carbon derived from the induced carbon substrate is determined by subtracting the amount of carbon derived from microorganisms from the total carbon amount. That is, assuming that the C/N ratio of microorganisms during culture is constant, the C/N ratio of microorganisms calculated by measuring the microorganism sample during seed culture and the amount of nitrogen in the dry solid content. From this, the amount of carbon derived from microorganisms in the dry solid content is calculated. The difference between the total carbon content of the dry solid content and the carbon content derived from microorganisms is calculated as the carbon content derived from the induced carbon substrate, and by dividing this by the amount of the culture, the carbon derived from the induced carbon substrate in the culture is calculated. Concentration is required.
(2) Next, determine the difference between the carbon concentrations derived from the induced carbon substrate calculated at two different time points. The difference value reflects the concentration change in carbon concentration from the induced carbon substrate in the culture between the two time points. Therefore, by calculating the concentration change per unit time from the difference value, the supply rate of the induced carbon substrate to the culture [g-carbon derived from the induced carbon substrate/L-culture solution/h] can be determined. .
本発明において、流加される非誘導炭素基質の供給速度は、単位時間当たりに培養物に流加される非誘導炭素基質由来の炭素の量として定義される。例えばフィードコントローラなどで設定された流加量と、流加される水溶液中の非誘導炭素基質濃度に基づいて、非誘導炭素基質の供給速度[g-非誘導炭素基質由来の炭素/L-培養液/h]を決定することができる。 In the present invention, the feed rate of fed uninduced carbon substrate is defined as the amount of carbon from the uninduced carbon substrate fed into the culture per unit time. For example, the feed rate of the non-induced carbon substrate [g-carbon derived from the non-induced carbon substrate/L-culture liquid/h] can be determined.
あるいは本発明において、流加される場合の誘導炭素基質の供給速度は、単位時間当たりに培養物に流加される誘導炭素基質由来の炭素の量として定義される。また、本発明において、バッチ添加される非誘導炭素基質の供給速度は、培養物中の非誘導炭素基質由来の炭素の単位時間当たりの濃度変化(消失速度)として定義される。該流加及びバッチ添加される炭素基質の供給速度の具体的な算出手順は、上述したとおりである。 Alternatively, in the present invention, the feed rate of the induced carbon substrate when fed-batch is defined as the amount of carbon from the induced carbon substrate that is fed into the culture per unit time. Furthermore, in the present invention, the feed rate of the batch-added non-induced carbon substrate is defined as the concentration change (disappearance rate) per unit time of carbon derived from the non-induced carbon substrate in the culture. The specific calculation procedure for the feeding rate of the carbon substrate added in fed-batch and batchwise manner is as described above.
本発明の方法において、微生物の培養のための諸条件は、上述した炭素基質の供給速度以外は、該微生物の種や、培養のスケールなどに合わせて、常法に従って適宜設定することができる。例えば、培養に用いる培養槽は、従来公知のものを適宜採用することができる。具体的には、フラスコ、通気撹拌型培養槽、気泡塔型培養槽、及び流動床型培養槽等が挙げられ、好ましくは、通気撹拌型培養槽である。培養温度は、例えば微生物が糸状菌の場合、好ましくは25~35℃、より好ましくは28±2℃である。培養物のpHは、例えば微生物が糸状菌の場合、好ましくはpH3~7、より好ましくはpH3.5~6に維持される。培養物のpH調整は、アンモニア等の通常のpH調整剤によって行われ得る。本発明における培養物のpHは、培養温度28℃において測定された値をいう。培養物のpHは、培養槽に備え付けた電極で測定することができる。培養期間は、4~10日間が好ましい。 In the method of the present invention, conditions for culturing the microorganisms, other than the above-mentioned supply rate of the carbon substrate, can be appropriately set according to the species of the microorganisms, the scale of the culture, etc. according to conventional methods. For example, conventionally known culture tanks can be used as appropriate for the culture tank. Specific examples include flasks, aeration-stirring type culture tanks, bubble column type culture tanks, and fluidized bed type culture tanks, with aeration-stirring type culture tanks being preferred. For example, when the microorganism is a filamentous fungus, the culture temperature is preferably 25 to 35°C, more preferably 28±2°C. For example, when the microorganism is a filamentous fungus, the pH of the culture is preferably maintained at pH 3 to 7, more preferably at pH 3.5 to 6. Adjustment of the pH of the culture can be carried out with conventional pH adjusting agents such as ammonia. The pH of the culture in the present invention refers to a value measured at a culture temperature of 28°C. The pH of the culture can be measured with an electrode attached to the culture tank. The culture period is preferably 4 to 10 days.
培養後、培養物から目的のセルラーゼを回収する。糸状菌セルラーゼ等の分泌型セルラーゼの場合、培養上清からセルラーゼを回収することができる。セルラーゼが細胞中に含まれている場合、細胞を破壊してセルラーゼを含む画分を取り出し、セルラーゼを回収することができる。セルラーゼの回収は、当該分野で通常使用される方法、例えば、傾斜法、膜分離、遠心分離、電気透析法、イオン交換樹脂の利用、蒸留、塩析等、又はこれらの組み合わせにより、行うことができる。回収したセルラーゼを、さらに単離又は精製してもよい。 After culturing, the desired cellulase is collected from the culture. In the case of secreted cellulase such as filamentous fungal cellulase, the cellulase can be recovered from the culture supernatant. If cellulase is contained in the cell, the cellulase can be recovered by disrupting the cell and removing a fraction containing the cellulase. Cellulase can be recovered by methods commonly used in the field, such as gradient method, membrane separation, centrifugation, electrodialysis, use of ion exchange resins, distillation, salting out, etc., or a combination thereof. can. The recovered cellulase may be further isolated or purified.
目的のセルラーゼが培養上清中に分泌される分泌型セルラーゼの場合、本発明でセルラーゼの製造に使用された微生物は、繰り返し使用することができる。すなわち、培養上清と分離した微生物細胞を回収し、これを新たな培地で誘導炭素基質と非誘導炭素基質の存在下で培養することで、再びセルラーゼを製造することができる。 When the target cellulase is a secreted cellulase that is secreted into the culture supernatant, the microorganism used to produce the cellulase in the present invention can be used repeatedly. That is, by collecting the culture supernatant and the separated microbial cells and culturing them in a new medium in the presence of an induced carbon substrate and a non-induced carbon substrate, cellulase can be produced again.
本発明のセルラーゼの製造方法は、微生物の培養と、培養物に蓄積したセルラーゼの回収及び培地の入れ替えとを交互に行う回分式方法であってもよく、又は、一部の微生物と培地を断続的もしくは連続的に入れ替えながら微生物の培養とセルラーゼの回収とを並行して行う半回分式もしくは連続的な方法であってもよい。 The method for producing cellulase of the present invention may be a batch method in which culturing of microorganisms, collection of cellulase accumulated in the culture and replacement of the medium are performed alternately, or a method in which some of the microorganisms and the medium are intermittent. It may be a semi-batch method or a continuous method in which microorganism culture and cellulase recovery are performed in parallel while changing the culture medium or continuously.
以下、実施例に基づき本発明をさらに詳細に説明するが、本発明はこれに限定されるものではない。 Hereinafter, the present invention will be explained in more detail based on Examples, but the present invention is not limited thereto.
(1)培養条件
(菌種培養)
トリコデルマ・リーセイPC-3-7株をセルロース含有培地で培養することで、セルラーゼを生産した。種菌培養として500mLフラスコに培地50mLを加え、1×105個/mLとなるようPC-3-7株の胞子を植菌し、28℃、220rpm(PRECI社、PRXYg-98R)にて振とう培養した。培地組成は表1のとおりである。菌種培養は、2日間行った。
(1) Culture conditions (bacterial species culture)
Cellulase was produced by culturing Trichoderma reesei PC-3-7 strain in a cellulose-containing medium. Add 50 mL of medium to a 500 mL flask for seed culture, inoculate with spores of PC-3-7 strain at 1 x 10 5 cells/mL, and shake at 28°C and 220 rpm (PRECI, PRXYg-98R). Cultured. The medium composition is shown in Table 1. Bacterial species culture was carried out for 2 days.
(前培養)
初期培地は、粉末セルロース(KCフロックW400;日本製紙)2%、及び表2に示すその他の培地成分を含有した。該初期培地500mLを含む1L容ジャーファーメンターBMZ-P((株)バイオット)に、前記種菌培養液を10%(v/v%)植菌して1日間培養して前培養液を得た。ジャーファーメンターの設定は以下のとおりとした:温度28℃、通気量0.5vvm、pH:4.5±0.1、撹拌数はDO=3.0ppmを保つよう変動。10%(w/w%)のアンモニア水溶液により、培養液のpHが上記所定の範囲に維持されるように制御した。
(preculture)
The initial medium contained 2% powdered cellulose (KC Flock W400; Nippon Paper Industries) and other medium components shown in Table 2. A 1 L jar fermenter BMZ-P (Biot Co., Ltd.) containing 500 mL of the initial medium was inoculated with 10% (v/v%) of the seed culture solution and cultured for 1 day to obtain a preculture solution. . The settings of the jar fermenter were as follows: temperature 28°C, aeration rate 0.5 vvm, pH: 4.5 ± 0.1, and stirring frequency varied to maintain DO = 3.0 ppm. The pH of the culture solution was controlled to be maintained within the above predetermined range using a 10% (w/w%) ammonia aqueous solution.
(本培養)
初期培地は、粉末セルロース(KCフックW400;日本製紙)4%、及び表2に示すその他の培地成分を含有した。該初期培地1000mLを含む2L容ジャーファーメンターBMZ-P((株)バイオット)に、前記前培養液を1%(v/v%)植菌して7日間培養した。ジャーファーメンターの設定は以下のとおりとした:温度30℃、通気量1.0vvm、pH:4.5±0.1、撹拌数は可変で、DO=2.0ppmを保つよう設定した。10%(w/w%)のアンモニア水溶液により、培養液のpHが上記所定の範囲に維持されるように制御した。培養中、下記(2)~(3)の手順に従って、糸状菌の呼吸活性の変化率とセルロース供給速度を毎時測定した。フィードコントローラDFR((株)バイオット)により、60%(w/w%)グルコース水溶液量を流加した。グルコース水溶液の流加は、炭素濃度換算で0.15~0.50g/L-初期培地/hで開始し、その後、セルロース供給速度に対するグルコース供給速度の比[グルコース(非誘導炭素)供給速度]/[セルロース(誘導炭素)供給速度]が下記表3の値になるように流加量を制御した(比較例1、実施例1~3)。
(main culture)
The initial medium contained 4% powdered cellulose (KC Hook W400; Nippon Paper Industries) and other medium components shown in Table 2. A 2 L jar fermenter BMZ-P (Biot Co., Ltd.) containing 1000 mL of the initial medium was inoculated with 1% (v/v%) of the preculture solution and cultured for 7 days. The settings of the jar fermenter were as follows: temperature: 30° C., aeration rate: 1.0 vvm, pH: 4.5±0.1, stirring frequency was variable, and was set to maintain DO = 2.0 ppm. The pH of the culture solution was controlled to be maintained within the above predetermined range using a 10% (w/w%) ammonia aqueous solution. During the culture, the rate of change in the respiratory activity of the filamentous fungi and the cellulose supply rate were measured every hour according to the procedures (2) to (3) below. A 60% (w/w%) glucose aqueous solution was fed using a feed controller DFR (Biot Co., Ltd.). The feeding of the glucose aqueous solution is started at a carbon concentration of 0.15 to 0.50 g/L-initial medium/h, and then the ratio of the glucose feeding rate to the cellulose feeding rate [glucose (non-induced carbon) feeding rate] The feeding amount was controlled so that /[cellulose (induced carbon) supply rate] was the value shown in Table 3 below (Comparative Example 1, Examples 1 to 3).
(2)呼吸活性の測定
培養中、排ガス分析装置(DEX-1562A;株式会社バイオット)、及びバルブ付フローメータ(MODEL RK1200;コフロック株式会社)により、培養液中のCO2濃度(v/w%)と培養通気量(L/min)を毎時計測した。同時に培養液を5mL採取し、遠心分離(日立工機社製、himac CF7D2、ローター型式:RT3S3、ローター設置アダプタ:50mL 4×4本、チューブ寸法:直径36.5mm、長さ120mm、3,000rpm、15min)により上清と固形分を分離した。上清は0.45μmのフィルター(材質:セルロースアセテート)により濾過後、後述のセルラーゼ生産性測定に供した。固形分は15mLのイオン交換水にて2回遠心分離にて洗浄し、凍結乾燥した。乾燥物の固形分量を計量し、培養液の乾燥固形分濃度を算出した。
(2) Measurement of respiratory activity During the culture, the CO 2 concentration (v/w%) in the culture solution was measured using an exhaust gas analyzer (DEX-1562A; Biot Co., Ltd.) and a flow meter with a valve (MODEL RK1200; Cofloc Co., Ltd.). ) and culture aeration rate (L/min) were measured hourly. At the same time, 5 mL of culture solution was collected and centrifuged (manufactured by Hitachi Koki Co., Ltd., himac CF7D2, rotor model: RT3S3, rotor installation adapter: 50 mL 4 x 4 pieces, tube dimensions: diameter 36.5 mm, length 120 mm, 3,000 rpm) , 15 min) to separate the supernatant and solid content. The supernatant was filtered through a 0.45 μm filter (material: cellulose acetate) and then subjected to the cellulase productivity measurement described below. The solid content was washed twice with 15 mL of ion-exchanged water by centrifugation and freeze-dried. The solid content of the dried material was measured, and the dry solid content concentration of the culture solution was calculated.
培養液の乾燥固形分中の元素(窒素・炭素)量を、元素分析装置vario EL cube(エレメンタール社)を用いて測定した。測定した窒素量及び炭素量を培養物量で除することで、それぞれ培養液中の全窒素濃度及び全炭素濃度を得た。同様に、種菌培養時の糸状菌体サンプルを元素分析し、菌体のC/N比を算出した。該算出したC/N比(C:45%、N:7.9%、C/N比=5.7)に該乾燥固形分中の窒素濃度を掛け算することで、該乾燥固形分中の菌体由来の炭素量を算出した(式(4))。次いで、式(5)に従ってセルロース由来炭素濃度を求めた。さらに、乾燥菌体中の炭素量を45質量%として、式(6)により培養液中の菌体濃度(乾燥質量換算)を算出した。
菌体由来の炭素濃度[g-C/L]
= 乾燥固形分中のN濃度[g-N/L] × 5.7[菌体C/N比[g-C/g-N]] …(4)
セルロース由来炭素濃度[g-C/L]
= 乾燥固形分中全炭素濃度[g-C/L]-乾燥固形分中の菌体由来炭素濃度[g-C/L] …(5)
菌体濃度[g-dry cell/L-培養物]=菌体由来の炭素濃度[g-C/L] ÷ 0.45 …(6)
The amount of elements (nitrogen and carbon) in the dry solid content of the culture solution was measured using an elemental analyzer vario EL cube (manufactured by Elemental). By dividing the measured amounts of nitrogen and carbon by the amount of culture, the total nitrogen concentration and total carbon concentration in the culture solution were obtained, respectively. Similarly, a filamentous fungal cell sample obtained during seed culture was subjected to elemental analysis, and the C/N ratio of the fungal cells was calculated. By multiplying the calculated C/N ratio (C: 45%, N: 7.9%, C/N ratio = 5.7) by the nitrogen concentration in the dry solid content, The amount of carbon derived from the bacterial cells was calculated (Equation (4)). Next, the cellulose-derived carbon concentration was determined according to equation (5). Furthermore, assuming that the amount of carbon in the dried bacterial cells was 45% by mass, the bacterial cell concentration in the culture solution (in terms of dry mass) was calculated using equation (6).
Carbon concentration derived from bacterial cells [gC/L]
= N concentration in dry solid content [gN/L] × 5.7 [Bacterial cell C/N ratio [gC/gN]] …(4)
Cellulose-derived carbon concentration [gC/L]
= Total carbon concentration in dry solid content [gC/L] - Bacterial cell-derived carbon concentration in dry solid content [gC/L] …(5)
Bacterial cell concentration [g-dry cell/L-culture] = Bacterial cell-derived carbon concentration [gC/L] ÷ 0.45...(6)
下記式(1)’~(3)’に基づいて、糸状菌の呼吸活性の変化率を算出した。
呼吸活性[g-CO2/g-dry cell/h]
=(CO2排出速度[g-CO2/L-培養物/h])÷(菌体濃度[g-dry cell/L-培養物] …(1)’
ここで、
g-CO2 =(CO2濃度[vol%]÷100 × 培養通気量[L/min]×60[min])
÷(Vm × 44[CO2モル質量]) …(2)’
ここで、CO2濃度[vol%]:培養物中CO2濃度(vol%)
Vm:理想気体のモル体積=22.4
L-培養物:培養物量(L)
呼吸活性の変化率 ={|時間t2における呼吸活性 - 時間t1における呼吸活性|
÷(時間t1における呼吸活性)}(t2>t1, |t1-t2| = 1)…(3)’
The rate of change in the respiratory activity of filamentous fungi was calculated based on the following formulas (1)' to (3)'.
Respiratory activity [g-CO 2 /g-dry cell/h]
= (CO 2 excretion rate [g-CO 2 /L-culture/h]) ÷ (bacterial cell concentration [g-dry cell/L-culture] …(1)'
here,
g-CO 2 = (CO 2 concentration [vol%] ÷ 100 × culture aeration rate [L/min] × 60 [min])
÷(Vm × 44[CO 2 molar mass]) …(2)'
Here, CO 2 concentration [vol%]: CO 2 concentration in culture (vol%)
Vm: Molar volume of ideal gas = 22.4
L-Culture: Culture volume (L)
Rate of change in respiratory activity = {|Respiratory activity at time t 2 - Respiratory activity at time t 1 |
÷ (respiratory activity at time t 1 )} (t 2 > t 1 , | t 1 − t 2 | = 1)...(3)'
(3)炭素基質供給速度の測定
続いて、式(5)で求めたセルロース由来の炭素濃度を用いて、式(7)に基づいて培養液に対するセルロース供給速度を算出した。
セルロース供給速度[g-誘導炭素基質由来の炭素/L-培養液/h]
= 時間t2におけるセルロース由来の炭素濃度 - 時間t1におけるセルロース由来の炭素濃度(t2>t1, |t1-t2| = 1) …(7)
(3) Measurement of carbon substrate supply rate Next, using the cellulose-derived carbon concentration determined by formula (5), the cellulose supply rate to the culture solution was calculated based on formula (7).
Cellulose feed rate [g-carbon derived from derived carbon substrate/L-culture solution/h]
= Cellulose-derived carbon concentration at time t 2 - Cellulose-derived carbon concentration at time t 1 (t 2 > t 1 , | t 1 − t 2 | = 1) …(7)
グルコース供給速度は、フィードコントローラの設定値[グルコース水溶液/h]を基に算出した。水溶液中グルコース濃度を60w/w%、グルコース中の炭素の質量割合を0.4(72/180、ここでグルコースのモル質量180g/mol、グルコース中の炭素のモル質量12×6=72g/mol)として、式(8)に基づいて培養液に対するグルコースの供給速度を算出した。
グルコース供給速度[g-非誘導炭素基質由来の炭素/L-培養物/h]
= フィードコントローラの設定値[g-グルコース水溶液/h]×水溶液中グルコース濃度(%)×グルコース中の炭素の質量割合÷培養物量[L]
= フィードコントローラの設定値[g/h]×0.6×0.4÷培養物量[L] …(8)
The glucose supply rate was calculated based on the setting value of the feed controller [glucose aqueous solution/h]. The concentration of glucose in the aqueous solution is 60 w/w%, the mass ratio of carbon in glucose is 0.4 (72/180, where the molar mass of glucose is 180 g/mol, the molar mass of carbon in glucose is 12 x 6 = 72 g/mol ), the supply rate of glucose to the culture solution was calculated based on equation (8).
Glucose feed rate [g-carbon from uninduced carbon substrate/L-culture/h]
= Feed controller setting value [g-glucose aqueous solution/h] × glucose concentration in aqueous solution (%) × mass ratio of carbon in glucose ÷ culture volume [L]
= Feed controller setting value [g/h] × 0.6 × 0.4 ÷ Culture volume [L] …(8)
(4)セルラーゼ生産性測定
(2)で取得した培養上清中のタンパク質濃度をBradford法にて定量し、セルラーゼ濃度とした。定量では、0.125~0.75mg/mLのウシγグロブリン(BGG)を標準物質とし、Quick start protein assay(standard assay)(Bio-Rad社製)により、マイクロプレートリーダー(Molecular Devices社製、VersaMax)にて595nmの吸光度を測定し、タンパク質濃度を計算した。得られた上清のタンパク質濃度[g-Protein/L]を、該上清のサンプリング時点までに供給された炭素濃度[g-C/L]で除することで糸状菌のセルラーゼ生産性[g-Protein/g-C]を算出した。比較例1の培養7日目のセルラーゼ生産性を100%としたときの、培養1~7日での比較例1、実施例1、実施例2及び実施例3の相対セルラーゼ生産性を求めた。比較例1及び実施例1~3の菌体の呼吸活性変化率及び炭素基質の供給速度比の変化、ならびに培養7日目の相対セルラーゼ生産性を表3に示す。また培養1~7日目の相対セルラーゼ生産性を表4及び図1に示す。
(4) Measurement of Cellulase Productivity The protein concentration in the culture supernatant obtained in (2) was quantified by the Bradford method and determined as the cellulase concentration. For quantitative determination, bovine gamma globulin (BGG) of 0.125 to 0.75 mg/mL was used as a standard substance, using a quick start protein assay (standard assay) (manufactured by Bio-Rad) and a microplate reader (manufactured by Molecular Devices, Inc.). VersaMax) to measure the absorbance at 595 nm and calculate the protein concentration. The cellulase productivity of filamentous fungi [g-Protein/L] is calculated by dividing the protein concentration [g-Protein/L] of the obtained supernatant by the carbon concentration [gC/L] supplied up to the time of sampling the supernatant. /gC] was calculated. Relative cellulase productivity of Comparative Example 1, Example 1, Example 2, and Example 3 was determined on days 1 to 7 of culture when the cellulase productivity on day 7 of culture of Comparative Example 1 was taken as 100%. . Table 3 shows the rate of change in respiration activity of the bacterial cells and the change in the carbon substrate supply rate ratio of Comparative Example 1 and Examples 1 to 3, as well as the relative cellulase productivity on the 7th day of culture. Furthermore, the relative cellulase productivity on days 1 to 7 of culture is shown in Table 4 and FIG. 1.
Claims (7)
セルロース及びグルコースの存在下でトリコデルマ菌を培養すること、及び
該トリコデルマ菌の呼吸活性を経時的に測定すること、
を含み、
該トリコデルマ菌の呼吸活性の変化率が0.1以上である期間において、下記式Aで表される比Rが100以下である、
式A:R=グルコースの供給速度/セルロースの供給速度
方法。 A method for producing cellulase, comprising:
culturing Trichoderma fungi in the presence of cellulose and glucose ; and
Measuring the respiratory activity of the Trichoderma bacteria over time;
including;
During the period in which the rate of change in the respiratory activity of the Trichoderma bacteria is 0.1 or more, the ratio R represented by the following formula A is 100 or less,
Formula A: R= Glucose Feed Rate/ Cellulose Feed Rate Method.
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| JP2014521359A (en) | 2011-08-19 | 2014-08-28 | イエフペ エネルジ ヌヴェル | Cellulase production method using filamentous fungus suitable for fermenter having low oxygen transfer capacity coefficient KLa |
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| SZABO, I. J. et al.,Optimized cellulase production by phanerochaete chrysosporium: control of catabolite repression by f,Journal of Biotechnology,1996年,vol.48,p.221-230 |
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