JP2003153686A - New microorganism and method for degrading persistent organochlorine compound - Google Patents

New microorganism and method for degrading persistent organochlorine compound

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Publication number
JP2003153686A
JP2003153686A JP2001353651A JP2001353651A JP2003153686A JP 2003153686 A JP2003153686 A JP 2003153686A JP 2001353651 A JP2001353651 A JP 2001353651A JP 2001353651 A JP2001353651 A JP 2001353651A JP 2003153686 A JP2003153686 A JP 2003153686A
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JP
Japan
Prior art keywords
dioxin
strain
dioxins
ability
aromatic compounds
Prior art date
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JP2001353651A
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Japanese (ja)
Other versions
JP4122422B2 (en
Inventor
Nobutada Kimura
信忠 木村
Akira Miyazaki
章 宮崎
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National Institute of Advanced Industrial Science and Technology AIST
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National Institute of Advanced Industrial Science and Technology AIST
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Abstract

PROBLEM TO BE SOLVED: To provide both a new microorganism having an excellent degrading ability for persistent aromatic compounds, especially chlorinated dioxins without requiring new other carbon sources as a nutrient source and a method for industrially and advantageously degrading the persistent aromatic compounds using the new miroorganism. SOLUTION: This NK32 strain of the genus Corynebacterium, especially a new strain has a degrading ability for the persistent aromatic compounds.

Description

【発明の詳細な説明】Detailed Description of the Invention

【0001】[0001]

【発明の属する技術分野】本発明は、難分解性有機塩素
化合物、特にダイオキシン類の分解能に優れた新規な微
生物およびこの微生物を用いた難分解性有機塩素化合物
の分解方法に関する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a novel microorganism having excellent decomposability of a persistent organochlorine compound, particularly dioxins, and a method for decomposing the persistent organochlorine compound using the microorganism.

【0002】[0002]

【従来の技術】難分解性ハロゲン化芳香族化合物、特に
ダイオキシン類は、人体に対して非常に高い毒性と催奇
性を示し、また疎水的な性質から食物連鎖による生物濃
縮が行われる。近年、これらのダイオキシン類が化学物
質の生成過程や廃棄物の燃焼過程で非意図的に生成し、
焼却灰や廃棄物処分場の浸出水などを介して拡散する地
球規模での環境汚染が大きな社会問題となっている。ダ
イオキシン類は熱処理や化学的処理により分解すること
が可能なものであるが、環境中、特に土壌や河川の底泥
などに低濃度で存在しており、その処理を前述の方法で
行った場合には、効率が悪くまた経済的にも負担が大き
い。
2. Description of the Related Art Persistent halogenated aromatic compounds, especially dioxins, exhibit extremely high toxicity and teratogenicity to the human body, and because of their hydrophobic nature, they are bioconcentrated by the food chain. In recent years, these dioxins are unintentionally produced during the production process of chemical substances and the combustion process of waste,
Global environmental pollution that diffuses through incinerated ash and leachate from waste disposal sites is a major social problem. Although dioxins can be decomposed by heat treatment or chemical treatment, they are present in the environment, especially in soil or bottom mud of rivers, at low concentrations, and when the treatment is performed by the above method. Is inefficient and economically burdensome.

【0003】このような問題を解決するために、微生物
を用いて塩化ダイオシキンを分解する方法が考えられ、
シュ−ドモナス、スフィンゴモナス属やテラバクター属
など、幾つかのダイオキシン分解能を有する微生物につ
いての報告がなされている。しかしながら、従来公知の
塩化ダイオキシン類分解生成物には、次のような問題点
があった。 分解機構として共代謝(コメタボリズム)を伴うた
め、その栄養源として他の炭素源を供給する必要があ
る。 高塩素化ダイオキシン類の分解能に劣る。
In order to solve such a problem, a method of decomposing diiochicin chloride using a microorganism has been considered,
There have been reports on some microorganisms having dioxin decomposing ability such as Pseudomonas, Sphingomonas and Terrabactor. However, the conventionally known decomposition products of dioxin chlorides have the following problems. Since co-metabolism is involved as a decomposition mechanism, it is necessary to supply another carbon source as its nutritional source. Poor resolution of highly chlorinated dioxins.

【0004】[0004]

【発明が解決しようとする課題】本発明は、上記事情に
鑑みてなされたものであり、その目的は、栄養源として
新たな他の炭素源を必要とせず、しかも難分解性芳香族
化合物特に塩化ダイオキシン類の分解能力に優れた新規
微生物およびこれを用いた難分解性芳香族化合物の工業
的に有利な分解方法を提供することにある。
SUMMARY OF THE INVENTION The present invention has been made in view of the above circumstances, and an object of the present invention is not to require another new carbon source as a nutritional source, and in particular, a persistent aromatic compound. It is an object of the present invention to provide a novel microorganism excellent in decomposing ability of dioxins chloride and an industrially advantageous decomposition method of a hardly decomposable aromatic compound using the same.

【0005】[0005]

【課題を解決するための手段】本発明者らは、前記課題
を解決するために有効な新規微生物を全国各地の土壌及
び産業排水処理場の活性汚泥等に求め探索した結果、コ
リネバクテリウム属の中の特定な菌株が有効であるとの
知見を得た。
[Means for Solving the Problems] The inventors of the present invention searched for new microorganisms effective for solving the above problems in soil and activated sludge of industrial wastewater treatment plants all over the country, and found that Corynebacterium sp. It was found that the specific strains of the above were effective.

【0006】即ち、本発明によれば、第一に、コリネバ
クテリウム属 NK32菌株が提供される。第二に、難
分解性芳香族化合物の分解能を有することを特徴とする
第一に記載の菌株が提供される。第三に、難分解性芳香
族化合物がダイオキシン類であることを特徴とする第二
に記載の菌株が提供される。第四に、ダイオキシン類が
塩素化ダイオキシン類であることを特徴とする第三に記
載の菌株が提供される。第五に、第一乃至第四に記載の
菌株を用いることを特徴とする難分解性芳香族化合物の
分解方法が提供される。第六に、難分解性芳香族化合物
がダイオキシン類であることを特徴とする第五に記載の
分解方法が提供される。第七に、ダイオキシン類が塩素
化ダイオキシン類であることを特徴とする第六に記載の
分解方法が提供される。
[0006] That is, according to the present invention, firstly, a Corynebacterium NK32 strain is provided. Secondly, the strain according to the first aspect is provided, which has the ability to decompose persistent aromatic compounds. Thirdly, there is provided the strain according to the second, wherein the hardly decomposable aromatic compound is dioxins. Fourth, there is provided the strain according to the third, wherein the dioxins are chlorinated dioxins. Fifth, there is provided a method for decomposing a hardly-decomposable aromatic compound, which comprises using the strains according to the first to fourth aspects. Sixth, the decomposition method according to the fifth is characterized in that the hardly decomposable aromatic compound is a dioxin. Seventh, there is provided the decomposition method according to the sixth, wherein the dioxins are chlorinated dioxins.

【0007】[0007]

【発明の実施の形態】本発明に係る新規微生物は、次の
ような行程によって天然から分離することにより得られ
る。全国30ヶ所から土壌、産業排水処理場の活性汚泥等
のサンプル約50点を採取し、まず、試験管に20ml の最
少培地(組成:1000mlあたり 4.1 g Na2HPO4・2H20;0.4
g KH2PO4; 0.5 g (NH4)2SO4; 0.1 g MgCl2・6H2O; 5
0 mg Ca(NO3)2・4H2O; 20 mg Fe(NH4)2- citrate, 0.1m
l a trace element solution without EDTA)と最終濃
度0.2 mM のジベンゾフランを加え、採取試料約0.1gを
加えて攪拌する。これを約1週間、30度にて培養し、試
験管内における培養液の色や濁度の変化を観察し、変化
のあった培養液から20μl を採取して、上記の組成の培
地に接種して培養し、この操作を5回繰り返し、ジベン
ゾフランを分解・資化する菌を検索した。培養にて抽出
した菌は0.2 mM のジベンゾフランを含む最少寒天培地
でコロニーを単一化する。この単一菌を0.1 mM 無塩化
ダイオキシンを含む液体最少培地で約7日間、30度にて
振盪培養する。これらの菌株からダイオキシンの分解・
資化能力を有するものとして得られた菌株が本発明に係
る新規微生物であり、コリネバクテリウム・ウレアリテ
ィクム NK32株と命名する。この菌株は、茨城県内で採
取されたサンプル(土壌)から分離されたもので、独立
行政法人産業技術総合研究所 特許生物寄託センターに
寄託されており、その受託番号はFERM P-18501である。
BEST MODE FOR CARRYING OUT THE INVENTION The novel microorganism of the present invention can be obtained by separating it from nature by the following steps. Soil nationwide 30 locations, samples were taken approximately 50 points, such as activated sludge industrial waste water treatment plant, first, minimal medium 20ml test tube (composition: 1000 ml per 4.1 g Na 2 HPO 4 · 2H 2 0; 0.4
g KH 2 PO 4 ; 0.5 g (NH 4 ) 2 SO 4 ; 0.1 g MgCl 2・ 6H 2 O; 5
0 mg Ca (NO 3) 2 · 4H 2 O; 20 mg Fe (NH 4) 2 - citrate, 0.1m
la trace element solution without EDTA) and dibenzofuran at a final concentration of 0.2 mM, add about 0.1 g of the sample and stir. Incubate this at 30 ° C for about 1 week, observe the change in the color and turbidity of the culture medium in a test tube, collect 20 μl from the changed culture medium, and inoculate it into the medium of the above composition. Then, this operation was repeated 5 times to search for a bacterium that decomposes and assimilates dibenzofuran. The bacteria extracted by culturing are single colonyed on a minimal agar medium containing 0.2 mM dibenzofuran. This single bacterium is cultured in a liquid minimal medium containing 0.1 mM unchlorinated dioxin for about 7 days at 30 ° C. with shaking. Decomposition of dioxin from these strains
The strain obtained as having assimilation ability is the novel microorganism of the present invention and is named Corynebacterium urealyticum NK32. This strain was isolated from a sample (soil) collected in Ibaraki prefecture, and has been deposited at the Patent Biological Depositary Center, National Institute of Advanced Industrial Science and Technology, and its deposit number is FERM P-18501.

【0008】次に、本発明に係る菌株の細菌学的性質を
以下に示す。 A. 形態 桿菌 V字形成 大きさ(μm):幅 1.0、長さ1.5〜3.0 B. 培地における生育状態 (1) 生育温度範囲:至適発育温度範囲は30度 C. 生理・生化学的性質 (1) グラム反応 : + (2) 運動性 : - (3) 好気性での発育 : + (4) 嫌気性での発育 : - (5) カタラーゼ反応 : + (6) オキシダーゼ反応 : + (7) O / F 試験 : - (8) 生育温度 : NT (9) 硫酸塩還元 : - (10) ピロジナミダーゼ : + (11) ピロリドニルアリルアミダーゼ : - (12) アルカリフォスファターゼ : - (13) βーグルクロニダーゼ : - (14) βーガラクトシダーゼ : + (15) αーグルコシダーゼ : - (16) N-アセチルーβーグルコサミニダーゼ : - (17) エスクリン(グルコシダーゼ) : + (18) ウレアーゼ : + (19) ゼラチンの液化 : - (20) 炭水化物の発酵性 グルコース : - マンニトール : - リボース : - キシロース : - マルトース : - 乳糖 : - 白糖 : - (21) グリコーゲン : - (22)ウレアーゼの加水分解性 : + (23)炭水化物からの酸産生 : +
Next, the bacteriological properties of the strain according to the present invention are shown below. A. Morphology V-form of bacillus Size (μm): width 1.0, length 1.5 to 3.0 B. Growth condition in medium (1) Growth temperature range: Optimal growth temperature range is 30 degrees C. Physiological and biochemical properties (1) Gram reaction: + (2) Motility:-(3) Aerobic growth: + (4) Anaerobic growth:-(5) Catalase reaction: + (6) Oxidase reaction: + (7 ) O / F test:-(8) Growth temperature: NT (9) Sulfate reduction:-(10) Pyrosinamidase: + (11) Pyrrolidonyl allyl amidase:-(12) Alkaline phosphatase:-(13) β- Glucuronidase:-(14) β-galactosidase: + (15) α-glucosidase:-(16) N-acetyl-β-glucosaminidase:-(17) Esculin (glucosidase): + (18) Urease: + (19) Gelatin Liquefaction:-(20) Fermentability of carbohydrates Glucose:-Mannitol:-Ribose:-Xylose:- Maltose: - lactose: - sucrose: - (21) Glycogen: - (22) urease hydrolyzable: + (23) Acid production from carbohydrates: +

【0009】以上の諸性質をバージェイのマニュアル
オブ ディターミナティブ バクテリオロジー第8版
(Bergey’s Manual of Determinative Bacteriology,
8 thedition)に基づいて検索したところ、上記性質か
ら本菌はコリネバクテリウム属に属し、コリネバクテリ
ウム・ウレアリティクムに該当すると認められた。しか
し、本菌はコリネバクテリウム・ウレアリティクムに属
する公知の菌株とは黄色色素産生、β-ガラクトシダー
ゼ陽性、エスクリン加水分解陽性等に差異があり、新規
な菌株と考えられる。なお、本菌は、例えばLB 培地で
生育させた後に、350μl のグリセリンに750μl の生育
菌を入れ、良く攪拌した後に、-80℃にて維持するとい
った条件で、保存することができる。
The above-mentioned various properties are described by Berjay's manual.
8th Edition of Bergen's Manual of Determinative Bacteriology,
Based on the above properties, it was confirmed that this bacterium belongs to the genus Corynebacterium and corresponds to Corynebacterium urealyticum. However, this bacterium is different from known strains belonging to Corynebacterium urealyticum in yellow pigment production, β-galactosidase positive, esculin hydrolysis positive, and the like, and is considered to be a novel strain. The bacterium can be stored, for example, after growing it in LB medium, adding 750 μl of the bacterium to 350 μl of glycerin, stirring it well, and maintaining it at −80 ° C.

【0010】本発明に係る新規微生物は、難分解性芳香
族化合物に対して、優れた資化能力と分解能力を示す。
対象となる難分解性芳香族化合物としては、芳香環を有
する化合物の全て包含され、単素環あるいは複素環の何
れであってもよく、またハロゲン、水酸基、カルボキシ
ル基などで置換されていてもよい。
The novel microorganism according to the present invention exhibits excellent assimilation ability and decomposition ability with respect to a hardly decomposable aromatic compound.
The target hardly-decomposable aromatic compound includes all compounds having an aromatic ring, may be either a homocyclic ring or a heterocyclic ring, and may be substituted with a halogen, a hydroxyl group, a carboxyl group or the like. Good.

【0011】単素環としては、ベンゼン;クロロベンゼ
ン等の置換基を有するベンゼン;安息香酸;フェノー
ル;カテコール;サリチル酸;インドール;トルエン等
が挙げられる。また複素環としては、ダイベンゾチオフ
ェン;フルオレン−9−オン;キサンテン;ビフェニ
ル;フルオレン;ベンゾフェノン;キサンテン−9−オ
ン;アントロン;ナフタレン;ダイベンゾスベレノンな
どが包含される。
Examples of the monocyclic ring include benzene, benzene having a substituent such as chlorobenzene, benzoic acid, phenol, catechol, salicylic acid, indole and toluene. Examples of the heterocycle include dibenzothiophene; fluorene-9-one; xanthene; biphenyl; fluorene; benzophenone; xanthene-9-one; anthrone; naphthalene; dibenzosuberenone.

【0012】また、本発明の対象となる難分解性芳香族
化合物には、ジベンゾフラン、PCDDs(ポリ塩化ジ
ベンゾダイオキシン類)やPCDFs(ポリ塩化ジベン
ゾフラン類)等に代表されるダイオキシン類も包含され
る。
The hardly decomposable aromatic compounds to which the present invention is applied include dioxines represented by dibenzofuran, PCDDs (polychlorinated dibenzodioxins) and PCDFs (polychlorinated dibenzofurans).

【0013】特に、本発明に係る新規微生物は、後記実
施例に示されるように、PCDDs(ポリ塩化ジベンゾ
ダイオキシン類)やPCDFs(ポリ塩化ジベンゾフラ
ン類)等に代表される塩素化ダイオキシン類と環境中で
共存すると言われているジベンゾ−p−ダイオキシンを
栄養源として増殖し、塩素化ダイオキシン類の中でも極
めて毒性の高い、2,3,7,8の何れかの位置に塩素
が置換されたダイオキシン類の分解能に優れたものであ
る。
In particular, the novel microorganisms according to the present invention, as will be shown in the Examples below, are in the environment with chlorinated dioxins represented by PCDDs (polychlorinated dibenzodioxins) and PCDFs (polychlorinated dibenzofurans). , Which is said to coexist with dibenzo-p-dioxin, is a highly toxic chlorinated dioxin, and is dioxins in which chlorine is substituted at any of positions 2, 3, 7 and 8. It has excellent resolution.

【0014】従って、本発明に係る新規微生物は、従来
のように、栄養源として新たな他の炭素源を必要とせ
ず、2,3,7,8の何れかの位置に塩素が置換された
ダイオキシン類を効率よく分解できるので、工業的に極
めて有用なものということができる。
Therefore, the novel microorganism according to the present invention does not require any other new carbon source as a nutrient source as in the conventional case, and chlorine is substituted at any position of 2, 3, 7 and 8. Since dioxins can be decomposed efficiently, it can be said to be extremely useful industrially.

【0015】[0015]

【実施例】以下、本発明に係る新規微生物の性質を試験
の結果に基づいて説明する。
EXAMPLES The properties of the novel microorganism according to the present invention will be described below based on the test results.

【0016】(1) ダイオキシンの資化能力 ダイオキシンの資化能力は次のような試験により判定し
た。0.1mMのダイベンゾ-p-ダイオキシンを含む液体最少
培地20mlに菌株を植菌し、30℃にて振盪培養する。培養
24時間ごとに培養液を採取し、培養液の濁度を分光光度
計 [ヒュレットパッカード社製HP8452] にて測定し
て、菌の生育の良否を観察し、資化能力の有無について
判定する。またコントロールとしてCorynebacterium gl
utamicumIAM 12435 を植菌したものを振盪培養した。本
試験の結果は、図1に示した。本発明に係る菌株コリネ
バクテリウム・ウレアリティクム(Corynebacterium ur
ealyticm)NK32株は、公知のCorynebacterium glutamic
um IAM 12435 と異なり、ジベンゾフランを栄養源とし
て生育することが認められ、ダイオキシンに対して優れ
た資化能力を有することが分かる。
(1) Dioxin assimilation ability Dioxin assimilation ability was determined by the following test. The strain is inoculated into 20 ml of a liquid minimal medium containing 0.1 mM dibenzo-p-dioxin and shake-cultured at 30 ° C. culture
A culture solution is collected every 24 hours, and the turbidity of the culture solution is measured by a spectrophotometer [HP8452 manufactured by Hurret Packard], and the quality of the growth of the bacteria is observed to determine whether or not there is an assimilation ability. . As a control, Corynebacterium gl
The inoculated utamicum IAM 12435 was shake-cultured. The results of this test are shown in FIG. The strain Corynebacterium urealyticum according to the present invention (Corynebacterium ur
ealyticm) NK32 strain is a known Corynebacterium glutamic
Unlike um IAM 12435, it is recognized that it grows with dibenzofuran as a nutrient source, which shows that it has an excellent assimilation ability for dioxin.

【0017】(2)芳香族化合物の資化能力 芳香族化合物の資化能力は次のような試験により判定し
た。0.2 mM の芳香族化合物を含む最少液体培地に菌株
を植菌し、30℃で約72 時間培養する。72時間培養した
後に菌の生育の良否を観察し、資化能力の有無について
判定する。本試験の結果は、表1に示すとおりであり、
本発明に係る菌株コリネバクテリウム・ウレアリティク
ム(Corynebacterium urealyticm)NK32株はダイベンゾ
チオフェン、ナフタレン、ビフェニルなどの複環の芳香
族化合物とともに、トルエン、ベンゼン、フェノールな
どの単環の芳香族化合物などを栄養源として生育が認め
られた。従って幅広い化合物に対して資化能力を有し、
既に知られている他の菌株より優れた芳香族化合物の資
化能力を有することが分かる。
(2) Assimilation capacity of aromatic compounds The assimilation capacity of aromatic compounds was determined by the following test. Inoculate the strain in a minimal liquid medium containing 0.2 mM of aromatic compounds and incubate at 30 ° C for about 72 hours. After culturing for 72 hours, the quality of the growth of the bacterium is observed and the presence or absence of assimilation ability is judged. The results of this test are shown in Table 1,
The strain Corynebacterium urealyticm NK32 strain according to the present invention is a monocyclic aromatic compound such as toluene, benzene or phenol, together with a dicyclic thiophene, naphthalene, a bicyclic aromatic compound such as biphenyl, etc. Growth was recognized with the nutrient source. Therefore, it has the ability to assimilate a wide range of compounds,
It can be seen that it has a better assimilation ability of aromatic compounds than other strains already known.

【0018】[0018]

【表1】 [Table 1]

【0019】(3)塩化ダイオキシンの分解試験 本試験は各種ダイオキシンの異性体の分解性を調査する
ために行ったものであり、次のような手順による。本発
明に係る菌(Corynebacterium urealyticm NK32)をシ
ャーレから1白金耳採取し、最少培地50 ml を入れた培
養フラスコ(容量100ml )に添加する。これを30 ℃で7
2 時間振盪培養(120rpm) する。この培養液を6,000rp
m で15 分間の遠心分離にかけ、菌体を集めて燐酸バフ
ァー (pH7.5) で3回洗浄する。そして、最少培地5ml
が入った培養フラスコ(容量50ml)に塩化ダイオキシン
1ppm を入れ、上記菌体を加える。これを30℃で7日
間振盪培養する。
(3) Dioxin Chloride Decomposition Test This test was conducted to investigate the decomposability of various dioxin isomers, and the procedure is as follows. One platinum loop of the bacterium of the present invention (Corynebacterium urealyticm NK32) is collected from a petri dish and added to a culture flask (capacity 100 ml) containing 50 ml of a minimal medium. 7 at 30 ° C
Incubate with shaking (120 rpm) for 2 hours. This culture solution is 6,000rp
Centrifuge at m for 15 minutes, collect the cells, and wash 3 times with phosphate buffer (pH 7.5). And 5 ml of minimal medium
Add 1 ppm of dioxin chloride to a culture flask (capacity 50 ml) containing and add the above cells. This is shake-cultured at 30 ° C. for 7 days.

【0020】培養後、培養液に5 ml の酢酸エチルを加
えて塩化ダイオキシンを抽出する。得られた抽出液のう
ち、1ml を窒素ガスの噴射によって濃縮する。この液中
の塩化ダイオキシンをガスクロマトグラフーマススペク
トロメータ(GC-MS)[ヒューレットパッカード社製HP58
90, HP5971A] を用いて分析を行う。カラムとしては内
径0.25mm×長さ30m カラムDB5 を用いた。昇温条件は8
0〜280℃まで10分間で昇温させる。また、ヘリウ
ムガスの流量は0.8 ml/minにて行う。なお、塩化ダイオ
キシンの分解成分の同定及び定量にはおのおの市販の標
準品を用いることができる。本試験による分解率を次の
式によって算出し、その分解試験結果を表2に示す。
After culturing, 5 ml of ethyl acetate is added to the culture broth to extract dioxin chloride. Of the obtained extract, 1 ml is concentrated by jetting nitrogen gas. Dioxin chloride in this solution was analyzed for gas chromatograph mass spectrometer (GC-MS) [Hewlett-Packard HP58
90, HP5971A]. A column DB5 with an inner diameter of 0.25 mm and a length of 30 m was used as the column. Temperature rising condition is 8
The temperature is raised from 0 to 280 ° C. in 10 minutes. The flow rate of helium gas is 0.8 ml / min. A commercially available standard product can be used to identify and quantify the decomposition components of dioxin chloride. The decomposition rate in this test was calculated by the following formula, and the results of the decomposition test are shown in Table 2.

【0021】[0021]

【式1】分解率(%)=(検出塩素化ダイオキシン量/
添加ダイオキシン量)×100
[Formula 1] Decomposition rate (%) = (Detected chlorinated dioxin amount /
Added dioxin amount) x 100

【0022】[0022]

【表2】 [Table 2]

【0023】一般に、塩化ダイオキシンには塩素の置換
している数や位置によって、75種類の異性体が存在
し、毒性の高いものは2,3,7,8の何れかの位置、特に
ジ、トリテトラ体であり、微生物によるダイオキシンの
分解能力はダイオキシン分子中の塩素の数が多くなるに
従いその能力が低減すると言われているが、本菌は塩素
の置換数(モノ置換)が1の場合よりも複数(ポリ置
換)のものすなわち毒性の高いダイオキシンに対してそ
の分解能力が向上していることが分かる。また、3塩素
化に対しても分解性を有していることが分かる。
Generally, there are 75 kinds of isomers depending on the number and position of chlorine substitution in dioxin chloride, and the highly toxic one is 2,3,7,8, especially di-, It is a tritetra form, and it is said that the ability of microorganisms to decompose dioxin decreases as the number of chlorine in the dioxin molecule increases, but this bacterium has a chlorine substitution number (mono substitution) of 1 or more. It can be seen that even in the case of a plurality of (poly-substituted), that is, a highly toxic dioxin, its decomposition ability is improved. Further, it is understood that it also has a decomposability with respect to trichlorination.

【0024】[0024]

【発明の効果】以上説明したように、本発明に係る新規
微生物は、ダイオキシンや多くの種類の芳香族化合物の
資化能力を有するとともに、塩化ダイオキシンの高い分
解能力を有しているので、他の炭素源を加えることなし
に、汚染水や汚染土壌にて生育させ、維持することがで
きる。従って、河川水、下水等を汚染する塩化ダイオキ
シンの分解・処理、塩化ダイオキシンによって汚染され
た土壌等の浄化に用いることができる。また、この新規
微生物は、高塩化物、例えば3塩素化程度の塩化ダイオ
キシンに対して分解性を有し、高塩化物を含む汚染水や
汚染土壌の処理に用いることができ、さらに毒性を有す
る2,3,7,8,位へ塩素が置換した塩化ダイオキシンの分解
処理に用いることができる。
As described above, the novel microorganism according to the present invention has the ability to assimilate dioxin and many kinds of aromatic compounds and also has a high ability to decompose dioxin chloride. It can be grown and maintained in contaminated water or contaminated soil without adding any carbon source. Therefore, it can be used for decomposing and treating dioxin chloride that pollutes river water, sewage, etc., and for cleaning soil and the like contaminated with dioxin chloride. Further, this novel microorganism has degradability with respect to high chloride, for example, dichlorinated chloride having a degree of trichlorination, and can be used for treating contaminated water and contaminated soil containing high chloride, and further has toxicity. It can be used for decomposing dioxin chloride with chlorine substituted at the 2,3,7,8 position.

【図面の簡単な説明】[Brief description of drawings]

【図1】ダイオキシンを栄養源として生育するコリネバ
クテリウム・ウレアリティクム (Corynebacterium ure
alyticm)NK32 株の増殖曲線のグラフである。
[Fig. 1] Corynebacterium ureaticum that grows with dioxin as a nutrient source
alyticm) NK32 strain growth curve graph.

フロントページの続き (51)Int.Cl.7 識別記号 FI テーマコート゛(参考) C07D 319/24 C12R 1:15 //(C12N 1/20 B09B 3/00 ZABE C12R 1:15) Front page continuation (51) Int.Cl. 7 identification code FI theme code (reference) C07D 319/24 C12R 1:15 // (C12N 1/20 B09B 3/00 ZABE C12R 1:15)

Claims (7)

【特許請求の範囲】[Claims] 【請求項1】コリネバクテリウム属 NK32菌株。1. A Corynebacterium NK32 strain. 【請求項2】難分解性芳香族化合物の分解能を有するこ
とを特徴とする請求項1記載の菌株。
2. The strain according to claim 1, which has the ability to decompose persistent aromatic compounds.
【請求項3】難分解性芳香族化合物がダイオキシン類で
あることを特徴とする請求項2記載の菌株。
3. The strain according to claim 2, wherein the hardly decomposable aromatic compound is dioxins.
【請求項4】ダイオキシン類が塩素化ダイオキシン類で
あることを特徴とする請求項3に記載の菌株。
4. The strain according to claim 3, wherein the dioxins are chlorinated dioxins.
【請求項5】請求項1乃至4に記載の菌株を用いること
を特徴とする難分解性芳香族化合物の分解方法。
5. A method for decomposing a hardly decomposable aromatic compound, which comprises using the strain according to any one of claims 1 to 4.
【請求項6】難分解性芳香族化合物がダイオキシン類で
あることを特徴とする請求項5記載の分解方法。
6. The decomposition method according to claim 5, wherein the hardly decomposable aromatic compounds are dioxins.
【請求項7】ダイオキシン類が塩素化ダイオキシン類で
あることを特徴とする請求項6記載の分解方法。
7. The decomposition method according to claim 6, wherein the dioxins are chlorinated dioxins.
JP2001353651A 2001-11-19 2001-11-19 Novel microorganism and method for degrading chlorinated dioxins Expired - Lifetime JP4122422B2 (en)

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Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR20210030547A (en) * 2019-09-09 2021-03-18 주식회사 비제이씨 Method for purifying soil contaminated by dioxane

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR20210030547A (en) * 2019-09-09 2021-03-18 주식회사 비제이씨 Method for purifying soil contaminated by dioxane
WO2021049745A1 (en) * 2019-09-09 2021-03-18 주식회사 비제이씨 Method for purifying dioxin-contaminated soil
KR102231144B1 (en) * 2019-09-09 2021-03-24 주식회사 비제이씨 Method for purifying soil contaminated by dioxane

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