JP2007282631A - Microorganism having degrading and assimilating ability for triazine-based compound - Google Patents
Microorganism having degrading and assimilating ability for triazine-based compound Download PDFInfo
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本発明は、廃水処理等で難分解物質とされるトリアジン系化合物を分解資化する能力を有する新規な微生物に関する。 The present invention relates to a novel microorganism having an ability to decompose and assimilate triazine compounds which are hardly decomposed in wastewater treatment and the like.
従来、塗料工場から排出される塗料廃水などの工場廃水、農業廃水などの有機物を多く含む廃水は、凝集分離処理や限外濾過などの物理的処理を行った後、活性汚泥法により好気性条件下で生物処理されるのが一般的である(例えば、特許文献1参照)。しかしながら、通常の活性汚泥法では、微生物が有機物を分解する能力に限界があり、この手法では難分解性の有機物、例えばトリアジン系化合物などはそのまま処理水中に残存し、汚染物質として環境に残留する。 Conventionally, industrial wastewater such as paint wastewater discharged from paint factories and wastewater containing a large amount of organic matter such as agricultural wastewater are subjected to physical treatment such as coagulation separation treatment and ultrafiltration, and then aerobic conditions using the activated sludge method. In general, biological treatment is performed under the condition (see, for example, Patent Document 1). However, in the normal activated sludge method, there is a limit to the ability of microorganisms to decompose organic matter, and in this method, difficult-to-decompose organic matters such as triazine compounds remain in the treated water as they are and remain in the environment as pollutants. .
一般に、トリアジン系の化合物は、塗料、光重合開始剤、紫外線吸収剤、金属処理剤、コンクリート製品用減水剤などの工業製品に含まれており、また、農薬、除草剤、防藻剤、防黴剤などの農業用または一般家庭用品にも多く含まれている。しかし、トリアジン系の化合物は難分解性であるために、工場から排出される工場廃水、農業廃水、家庭廃水などの処理水中に残存し、さらに、使用された農薬や除草剤が土中に染み込むことにより地下水中にも残存し、汚染物質となって環境に残留したり拡散することが問題となっている。 In general, triazine-based compounds are contained in industrial products such as paints, photopolymerization initiators, ultraviolet absorbers, metal treatment agents, and water reducing agents for concrete products. It is also abundant in agricultural and general household products such as glazes. However, because triazine compounds are difficult to decompose, they remain in treated water such as factory wastewater, agricultural wastewater, and household wastewater discharged from the factory, and the used agricultural chemicals and herbicides penetrate into the soil. As a result, it remains in the groundwater, and it becomes a problem that it remains in the environment or diffuses as a pollutant.
また、トリアジン系化合物は、水中での安定性がかなり高く、20℃でpH5〜9の水溶液中では分解せず、内分泌攪乱作用があると言われており、人体への影響が心配されている。 In addition, triazine compounds are considerably stable in water, are not decomposed in an aqueous solution at pH 5-9 at 20 ° C., and are said to have endocrine disrupting effects. .
トリアジン系化合物、特にメラミンやメラミン樹脂などのメラミン誘導体を分解処理する方法として、特許文献2には、メラミンの水溶液または懸濁液を嫌気性条件下でメラミナーゼ活性をもつ微生物又は酵素剤に接触させることによってメラミンを生物学的に減成する方法が開示されている。また、特許文献3及び特許文献4には、トリアジン系化合物を好気性条件下でシュウドモナス(Pseudomonas)属またはロドコッカス(Rhodococcus)属のある種の菌株に接触させることにより分解する方法が開示されている。さらに、特許文献5には、世界中で多用されているトリアジン系農薬をベータプロテオバクテリアに属する細菌及び/またはこれを含む複合微生物系を用いて分解する方法が開示されている。 As a method for decomposing triazine compounds, particularly melamine derivatives such as melamine and melamine resins, Patent Document 2 discloses that an aqueous solution or suspension of melamine is brought into contact with a microorganism or enzyme agent having melaminease activity under anaerobic conditions. Thus, a method for biological degradation of melamine is disclosed. Patent Document 3 and Patent Document 4, a method of decomposing by contacting the triazine compound in certain strains of Pseudomonas (Pseudomonas) genus or Rhodococcus (Rhodococcus) genus under aerobic conditions is disclosed . Furthermore, Patent Document 5 discloses a method for degrading triazine-based pesticides that are frequently used all over the world, using bacteria belonging to beta-proteobacteria and / or complex microbial systems containing the same.
本発明の目的は、排水等の液体中に含まれるトリアジン系化合物、特にメラミンやメラミン樹脂などのメラミン誘導体の資化分解能を有する新規な微生物を提供することである。 An object of the present invention is to provide a novel microorganism having the ability to assimilate triazine-based compounds contained in liquids such as waste water, particularly melamine derivatives such as melamine and melamine resins.
本発明者らは、トリアジン系化合物を窒素源として増殖可能な微生物、すなわちトリア
ジン系化合物の資化分解能を有する微生物に着目し、種々スクリーニングを行い、今回、塗装排水処理リアクターから得られるトリアジン系化合物の1種であるメラミンを分解する菌群の中からメラミン分解能を持つ菌体を分離し、得られた菌体を同定したところ、アグロバクテリウム(Agrobacterium)属、ミクロバクテリウム(Microbacterium)属、オクロバクトラム(Ochrobactrum)属及びファイロバクテリウム(Phyllobacterium)属の4つの属に属する微生物がメラミンを分解する優れた能力を有していることを見出し、本発明を完成するに至った。
The present inventors focused on microorganisms that can be grown using triazine compounds as a nitrogen source, that is, microorganisms that have the ability to assimilate triazine compounds, and conducted various screenings. This time, triazine compounds obtained from a paint wastewater treatment reactor From the group of bacteria that decompose melamine, the melamine-degrading microbial cells were isolated and the obtained microbial cells were identified. The genus Agrobacterium , Microbacterium , The inventors have found that microorganisms belonging to the four genera of the genus Ochrobactrum and Phyllobacterium have excellent ability to degrade melamine, and have completed the present invention.
かくして、本発明は、アグロバクテリウム(Agrobacterium)属、ミクロバクテリウム(Microbacterium)属、オクロバクトラム(Ochrobactrum)属またはファイロバクテリウム(Phyllobacterium)属に属するトリアジン系化合物の分解資化能を有する微生物を提供するものである。 Thus, the present invention provides a microorganism having a decomposition utilization ability of Agrobacterium (Agrobacterium) genus-mycobacterial (Microbacterium) genus Ochrobactrum (Ochrobactrum) genus or Filo Agrobacterium (Phyllobacterium) triazine compounds belonging to the genus To do.
本発明の微生物は、工場廃水、農業廃水、家庭廃水などの液体中に含まれるトリアジン系化合物を分解資化し得るものであり、環境保全の面から非常に有用である。 The microorganism of the present invention can decompose and assimilate triazine compounds contained in liquids such as factory wastewater, agricultural wastewater, and household wastewater, and is very useful from the viewpoint of environmental conservation.
本明細書において、「トリアジン系化合物」は、トリアジン環を1分子中に少なくとも1個有する化合物であり、例えば、メラミン、メラミン樹脂、シアヌール酸、イソシアヌール酸、硫酸メラミン、ポリリン酸メラミン、アンメリン、メラム、硫酸メラム、ベンズグアナミン、アセトグアナミン、フタロジグアナミン、サクシノグアナミン、メラミンシアヌレート、メラミンフォスフェート、ピロリン酸メラミン、ブチレンジグアナミン、ノルボルネンジグアナミン、トリグアナミン、ベンゾグアナミン、アセトグアナミン、メチレンジメラミン、エチレンジメラミン、トリメチレンジメラミン、テトラメチレンジメラミン、ヘキサメチレンジメラミン、1,3−ヘキシレンジメラミン、トリス(β−シアノエチル)イソシアヌレート等が挙げられ、特にメラミン及びメラミン樹脂が好適である。ここで、メラミン樹脂とは、メラミンにアルデヒド、殊にホルムアルデヒド及び/又はアルコールを反応させることにより得られる樹脂を包含し、例えば、メチルエーテル化メラミン、エチルエーテル化メラミン、ブチルエーテル化メラミン等のアルキルエーテル化メラミンやメチロール化メラミンなどを挙げることができる。 In the present specification, the “triazine-based compound” is a compound having at least one triazine ring in one molecule. For example, melamine, melamine resin, cyanuric acid, isocyanuric acid, melamine sulfate, melamine polyphosphate, ammelin, Melam, melam sulfate, benzguanamine, acetoguanamine, phthalodiguanamine, succinoguanamine, melamine cyanurate, melamine phosphate, melamine pyrophosphate, butylenediguanamine, norbornene diguanamine, triguanamine, benzoguanamine, acetoguanamine, methylenedimelamine , Ethylene dimamine, trimethylene melamine, tetramethylene dimamine, hexamethylene dimamine, 1,3-hexylene melamine, tris (β-cyanoethyl) isocyanurate, etc. Gerare, it is particularly preferred melamine and melamine resins. Here, the melamine resin includes a resin obtained by reacting melamine with an aldehyde, particularly formaldehyde and / or alcohol, and examples thereof include alkyl ethers such as methyl etherified melamine, ethyl etherified melamine, and butyl etherified melamine. Melamine or methylol melamine can be mentioned.
以下、本発明のトリアジン系化合物の資化分解能を有する微生物の単離培養及び同定についてさらに詳細に説明する。 Hereinafter, the isolation culture and identification of microorganisms having the ability to assimilate the triazine compound of the present invention will be described in more detail.
トリアジン系化合物の資化分解能を有する微生物の単離及び同定
本発明のトリアジン系化合物の資化分解能を有する微生物は、以下のようにしてスクリーニグすることにより得られたものである。
Isolation and identification of microorganisms capable of assimilating triazine compounds The microorganisms having the ability to assimilate triazine compounds of the present invention are obtained by screening as follows.
基本培地(組成:塩化ナトリウム 5g,リン酸水素二カリウム 1g,リン酸二水素カリウム 1.18g,硫酸マグネシウム7水和物 200mg,塩化カリウム 2.23g,メラミン 100mg,蒸留水 1L)を作製し、それに、コハク酸590mg/L(培地1−1)、またはコハク酸590mg/L及びn−ブタノール555mg/L(培地1−2)、またはコハク酸590mg/L及びエチレングリコールモノブチルエーテル590mg/L(培地1−3)、またはコハク酸590mg/L及びグルコース900mg/L(培地1−4)を炭素源として添加した4種の培地を調製し、孔径0.20μmのフィルターを用いて濾過滅菌した。 Prepare a basic medium (composition: sodium chloride 5 g, dipotassium hydrogen phosphate 1 g, potassium dihydrogen phosphate 1.18 g, magnesium sulfate heptahydrate 200 mg, potassium chloride 2.23 g, melamine 100 mg, distilled water 1 L), Also, succinic acid 590 mg / L (medium 1-1), or succinic acid 590 mg / L and n-butanol 555 mg / L (medium 1-2), or succinic acid 590 mg / L and ethylene glycol monobutyl ether 590 mg / L (medium 1-3) or four types of media supplemented with 590 mg / L of succinic acid and 900 mg / L of glucose (medium 1-4) as a carbon source were prepared and sterilized by filtration using a filter having a pore size of 0.20 μm.
一方、塗料製造工場の廃水処理施設から採取したスラッジを上記4種の各培地100mlに対して接種し、次いで、25℃、150rpmで振とう培養を行った。7日間培養後の各培地におけるメラミン濃度は図1に示すとおりであった。これらの培養においてメラ
ミンの減少が確認され、同時にアンモニア態窒素濃度の増加が確認された。この培養により、メラミンを分解する4種の菌群が得られた。各菌群をMD−1、MD−2、MD−3、MD−4と称する。
On the other hand, sludge collected from a wastewater treatment facility at a paint manufacturing plant was inoculated into 100 ml of each of the above four types of medium, and then cultured with shaking at 25 ° C. and 150 rpm. The melamine concentration in each medium after culturing for 7 days was as shown in FIG. In these cultures, a decrease in melamine was confirmed, and at the same time an increase in ammonia nitrogen concentration was confirmed. By this cultivation, four types of fungal groups that decompose melamine were obtained. Each fungal group is referred to as MD-1, MD-2, MD-3, MD-4.
上記方法によって得られたMD−1、MD−2、MD−3、MD−4のメラミン分解性菌群を以下の方法で培養し、分解菌群からメラミン分解性菌株を単離した。 MD-1, MD-2, MD-3, and MD-4 melamine-degrading bacterial groups obtained by the above method were cultured by the following method, and melamine-degrading bacterial strains were isolated from the degrading bacterial group.
培地2(組成:肉エキス 5g,ペプトン 10g,塩化ナトリウム 5g,寒天 15g,蒸留水 1L)を作製し、この培地2に各分解菌群の培養液を塗布し、30℃で2日間静置培養した。この培養で生育したコロニーを釣菌し、メラミンの分解性を有すると考えられる菌のコロニーを確認するための培地3(組成:塩化ナトリウム 5g,リン酸水素二カリウム 1g,リン酸二水素カリウム 1.18g,硫酸マグネシウム7水和物
200mg,塩化カリウム 2.23g,メラミン 100mg,寒天 15g,蒸留水 1L)に移植し、30℃、7日間静置培養を行った。培養の結果、各分解菌群の中から両培地で生育可能な菌株の存在が確認され、それらの菌株を常法で単離した。
Medium 2 (composition: meat extract 5 g, peptone 10 g, sodium chloride 5 g, agar 15 g, distilled water 1 L) was prepared, and the culture solution of each degrading bacterium group was applied to medium 2 and allowed to stand at 30 ° C. for 2 days. did. Culture medium 3 (composition: sodium chloride 5 g, dipotassium hydrogen phosphate 1 g, potassium dihydrogen phosphate 1 for catching the colonies grown in this culture and confirming the colonies of bacteria considered to have melamine degradability 18 g, magnesium sulfate heptahydrate 200 mg, potassium chloride 2.23 g, melamine 100 mg, agar 15 g, distilled water 1 L), and static culture was performed at 30 ° C. for 7 days. As a result of the culture, the presence of strains capable of growing on both media was confirmed from each group of degrading bacteria, and these strains were isolated by a conventional method.
かくして単離されたメラミン分解性菌株を以下の方法により同定した。 The melamine-degrading strain thus isolated was identified by the following method.
上記の如くして単離されたメラミン分解性菌株の形態的性質、培地における生育の様相及び生理学的性質を通常の方法で評価した。培養は特記しない限り30℃で実施した。生育した菌株の形態的性質、培地における生育の様相及び生理学的性質から4種の菌株の存在が確認された。これら4種の菌株の菌学的性質を下記表1〜表4に示す。また、これら4種の菌株の16S−rRNA遺伝子の分析をエヌシーアイエムビー・ジャパン社に依頼し、16S−rRNA遺伝子の塩基配列を決定した。これら4種の菌株の16S−rRNA遺伝子の塩基配列の両端のPCR用プライマ―配列を除いた約1500塩基の部分の塩基配列を配列表の配列番号1〜4に示す。さらに、近隣結合法(NJ法)により系統樹を作成し、比較したところ、4種の菌株は、Agrobacterium属、Microbacterium属、Ochrobacterium属及びPhyllobacterium属に分類される菌であると推定された。 The morphological properties, growth aspects and physiological properties of the melamine-degrading strains isolated as described above were evaluated by conventional methods. Culture was performed at 30 ° C. unless otherwise specified. The existence of four strains was confirmed from the morphological properties of the grown strains, the mode of growth in the medium and the physiological properties. The mycological properties of these four strains are shown in Tables 1 to 4 below. Moreover, the analysis of the 16S-rRNA gene of these four strains was requested to NC Japan, and the base sequence of the 16S-rRNA gene was determined. The base sequences of about 1500 bases excluding the PCR primer sequences at both ends of the base sequences of the 16S-rRNA genes of these four strains are shown in SEQ ID NOs: 1 to 4 in the sequence listing. Furthermore, when a phylogenetic tree was prepared by the neighborhood joining method (NJ method) and compared, it was estimated that the four strains were bacteria classified into the genus Agrobacterium , Microbacterium , Ochrobacterium, and Phyllobacterium .
上記の4種の菌株の形態的性質、培地における生育の様相、生理学的性質及び16S−rRNA遺伝子塩基配列の結果を総合的に解析すると、Agrobacterium属の微生物はアグロバクテリウム・チュメファシエンス(Agrobacterium tumefaciens)の菌株であり、Microbacterium属の微生物はミクロバクテリウム sp.(Microbacterium sp.)の菌株であり、Ochrobacterium属の微生物はオクロバクトラム・アンスロピ(Ochrobactrum anthropi)の菌株であり、そしてPhyllobacterium属の微生物はファイロバクテリウム・ミルシナセアラム(Phyllobacterium myrsinacearum)の菌株であると同定された。これらの菌株は、それぞれ、アグロバクテリウム・チュメファシエンス(Agrobacterium tumefaciens)MD5−YMTK、ミクロバクテリウム sp.(Microbacterium sp.)MD7−MNTY、オクロバクトラム・アンスロピ(Ochrobactrum anthropi)MD1−MTJY及びファイロバクテリウム・ミルシラセアラム(Phyllobacterium myrsinacearum)MD6−JKRHとして、International Patent Organism Depository,National Institute of
Advanced Industrial Science and Technologyに、それぞれ、受託番号FERM P−20719、FERM P−20721、FERM P−20718及びFERM P−20720として平成17年11月24日に受託(原寄託)され、そして平成18年10月23日に、BUDAPEST TREATY ON THE INTERNATIONAL RECOGNITION OF THE DEPOSIT OF MICROORGANISMS FOR THE PURPOSES OF PATENT PROCEDUREに基き、それぞれ、受託番号FERM BP−10709、FERM BP−10711、FERM
BP−10708及びFERM BP−10710として国際寄託に移管された。
Comprehensive analysis of the morphological properties, growth behavior in the medium, physiological properties and results of 16S-rRNA gene base sequence of the above four strains, the microorganisms of the genus Agrobacterium are Agrobacterium tumefaciens ( Agrobacterium tumefaciens ), Microbacterium sp. ( Microbacterium sp.) Strain, Ochrobacterium sp. Strain, Ochrobactrum anthropi strain, and Phyllobacterium sp. Has been identified as a strain of Phyllobacterium myrsinacearum . These strains are respectively Agrobacterium tumefaciens MD5-YMTK, Microbacterium sp. ( Microbacterium sp.) MD7-MNTY, Ochrobactrum anthropi MD1-MTJY and Phylobacteria As U.M.-Millsilarum ( Phyllobacterium myrsinacearum ) MD6-JKRH, International Patent Organism Depository, National Institute of
Deposited to Advanced Industrial Science and Technology as deposit numbers FERM P-20719, FERM P-20721, FERM P-20718 and FERM P-20720 on November 24, 2005 (original deposit), and in 2006 On October 23rd, based on BUDAPEST TREATY ON THE INTERNATIONAL RECOGNITION OF THE DEPOSIT OF MICROORGANISMS FOR THE PURPOSES OF PATENT PROCEDURE, accession numbers FERM BP-10709, FERM BP-10711, FERM, respectively
BP-10708 and FERM BP-10710 were transferred to the International Deposit.
以下、実施例により本発明を更に具体的に説明するが、本発明の範囲は以下の実施例のみに限定されるものではない。 EXAMPLES Hereinafter, although an Example demonstrates this invention further more concretely, the scope of the present invention is not limited only to a following example.
なお、実施例で使用する培地3の組成は、塩化ナトリウム 5g,リン酸水素二カリウム 1g,リン酸二水素カリウム 1.18g,硫酸マグネシウム7水和物 200mg,塩化カリウム 2.23g,メラミン 100mg,寒天 15g,蒸留水 1Lであり、基本培地の組成は、塩化ナトリウム 5g,リン酸水素二カリウム 1g,リン酸二
水素カリウム 1.18g,硫酸マグネシウム7水和物 200mg,塩化カリウム 2.23g,メラミン 100mg,蒸留水 1Lである。
In addition, the composition of the culture medium 3 used in the examples is 5 g of sodium chloride, 1 g of dipotassium hydrogen phosphate, 1.18 g of potassium dihydrogen phosphate, 200 mg of magnesium sulfate heptahydrate, 2.23 g of potassium chloride, 100 mg of melamine, Agar 15g, distilled water 1L, basic medium composition: sodium chloride 5g, dipotassium hydrogen phosphate 1g, potassium dihydrogen phosphate 1.18g, magnesium sulfate heptahydrate 200mg, potassium chloride 2.23g, melamine 100 mg, 1 L of distilled water.
実施例1:シアヌ−ル酸の分解性
シアヌール酸100mgを配合した培地3(以下、培地3−1という)を調製し、アグロバクテリウム・チュメファシエンス(Agrobacterium tumefaciens)MD5−YMTK
FERM BP−10709、ミクロバクテリウム sp.(Microbacterium sp.)MD7−MNTY FERM BP−10711、オクロバクトラム・アンスロピ(Ochrobactrum anthropi)MD1−MTJY FERM BP−10708及びファイロバクテリウム・ミルシラセアラム(Phyllobacterium myrsinacearum)MD6−JKRH FERM
BP−10710の4種の各菌株を植菌し、30℃、7日間静置培養を行った。各菌株の培養の結果、培地3−1にコロニーが確認された。
Example 1: Degradability of cyanuric acid A medium 3 (hereinafter referred to as medium 3-1) containing 100 mg of cyanuric acid was prepared, and Agrobacterium tumefaciens MD5-YMTK
FERM BP-10709, Microbacterium sp. MD7-MNTY FERM BP-10711, Ochrobactrum anthropi MD1-MTJY FERM BP-10708 and Phyllobacterium myrsin 6 -JKRH FERM
Four strains of BP-10710 were inoculated and subjected to static culture at 30 ° C. for 7 days. As a result of culturing each strain, colonies were confirmed in the medium 3-1.
この結果、上記4種の菌株はいずれもトリアジン環分解活性を有することが確認された。 As a result, it was confirmed that all four strains had triazine ring decomposition activity.
実施例2:メラミン樹脂の分解性
メラミン樹脂(サイメル325、サイテックインダストリー(株)製、メチルエーテル化メラミン樹脂、固形分80%)100mgを配合した培地3(以下、培地3−2という)を調製し、アグロバクテリウム・チュメファシエンス(Agrobacterium tumefaciens)MD5−YMTK FERM BP−10709、ミクロバクテリウム sp.(Microbacterium sp.)MD7−MNTY FERM BP−10711、オクロバクトラム・アンスロピ(Ochrobactrum anthropi)MD1−MTJY FERM BP−10708及びファイロバクテリウム・ミルシラセアラム(Phyllobacterium myrsinacearum)MD6−JKRH FERM BP−10710の4種の各菌株を植菌し、30℃、7日間静置培養を行った。各菌株の培養の結果、培地3−2にコロニーが確認された。
Example 2: Degradability of melamine resin Medium 3 (hereinafter referred to as medium 3-2) containing 100 mg of melamine resin (Cymel 325, manufactured by Cytec Industry Co., Ltd., methyl etherified melamine resin, solid content 80%) was prepared. Agrobacterium tumefaciens MD5-YMTK FERM BP-10709, Microbacterium sp. ( Microbacterium sp.) MD7-MNTY FERM BP-10711, Ochrobactrum anthropi MD1-MTJY Four strains of FERM BP-10708 and Phyllobacterium myrsinacearum MD6-JKRH FERM BP-10710 were inoculated and cultured at 30 ° C. for 7 days. As a result of culturing each strain, colonies were confirmed in the medium 3-2.
この結果、上記4種の菌株はいずれもトリアジン環分解活性を有することが確認された。 As a result, it was confirmed that all four strains had triazine ring decomposition activity.
実施例3
前述の分解菌群MD−1、MD−2、MD−3及びMD−4をそれぞれ遠心分離した(4℃で10分間、10000rpm)。このようにして得られた菌ペーストを基本培地で洗浄し、再度遠心分離した(4℃で10分間、10000rpm)。遠心分離後の上清液をとりだし、孔径0.20μmのフィルターで濾過して、上清液から完全に細胞を取り除いた濾液を得た。このようにして得られた菌ペースト及び濾液を基本培地に懸濁し、25℃、150rpmで振とう培養し、メラミン濃度の経日変化を追跡した。その結果を下記表5に示す。
Example 3
The aforementioned degrading bacteria group MD-1, MD-2, MD-3 and MD-4 were each centrifuged (10000 rpm for 10 minutes at 4 ° C). The fungus paste thus obtained was washed with a basic medium and centrifuged again (at 4 ° C. for 10 minutes, 10,000 rpm). The supernatant liquid after centrifugation was taken out and filtered through a filter having a pore size of 0.20 μm to obtain a filtrate from which cells were completely removed from the supernatant liquid. The bacterial paste and filtrate thus obtained were suspended in a basic medium and cultured with shaking at 25 ° C. and 150 rpm, and the daily change in melamine concentration was followed. The results are shown in Table 5 below.
この結果、菌のメラミン分解活性は細胞外の酵素によるものではなく、細胞内の酵素により発現されることが確認された。 As a result, it was confirmed that the melamine-degrading activity of the bacteria was not expressed by extracellular enzymes but expressed by intracellular enzymes.
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