JP2000093164A - New microorganism and dye decoloration using the same - Google Patents

New microorganism and dye decoloration using the same

Info

Publication number
JP2000093164A
JP2000093164A JP10270290A JP27029098A JP2000093164A JP 2000093164 A JP2000093164 A JP 2000093164A JP 10270290 A JP10270290 A JP 10270290A JP 27029098 A JP27029098 A JP 27029098A JP 2000093164 A JP2000093164 A JP 2000093164A
Authority
JP
Japan
Prior art keywords
dye
bacillus
decolorizing
microorganism
alkaline condition
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.)
Granted
Application number
JP10270290A
Other languages
Japanese (ja)
Other versions
JP3846062B2 (en
Inventor
Takuhei Kimura
拓平 木村
Tatsuo Tsuchida
達雄 土田
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Toray Industries Inc
Original Assignee
Toray Industries Inc
Priority date (The priority date 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 date listed.)
Filing date
Publication date
Application filed by Toray Industries Inc filed Critical Toray Industries Inc
Priority to JP27029098A priority Critical patent/JP3846062B2/en
Publication of JP2000093164A publication Critical patent/JP2000093164A/en
Application granted granted Critical
Publication of JP3846062B2 publication Critical patent/JP3846062B2/en
Anticipated expiration legal-status Critical
Expired - Fee Related legal-status Critical Current

Links

Landscapes

  • Coloring (AREA)
  • Chemical Or Physical Treatment Of Fibers (AREA)
  • Micro-Organisms Or Cultivation Processes Thereof (AREA)

Abstract

PROBLEM TO BE SOLVED: To obtain a microorganism belonging to genus bacillus having dye decoloring ability under an alkaline condition capable of decreasing the degree of pigmentation of a solution colored by dye, especially useful for processing or the like of dye wastewater used under high temperature and high alkaline condition. SOLUTION: This microorganism [e.g.; bacillus-sp. DA1 (deposited in National Institute of Bioscience and Human Technology as 16921) or the like] belongs to genus bacillus, has decoloring ability to dye at >=40 deg.C under alkaline condition, capable of reducing the degree of pigmentation of a solution colored by dye at middle to high temperature under alkaline condition, especially brings a remarkable effects on the processing of the dye wastewater used under high temperature and high alkaline condition. This new microorganism is obtained by adding and culturing samples of nationwide soils, compost, activated sludge or the like, in an agar medium including Reactive back 5 as an azo reactive dye, at 45 deg.C, separating microorganism forming an orange clear zone in the blue medium after 1 to 2 days, and repeating refinements.

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】本発明は新規な染料脱色微生
物および該微生物を用いた染料の脱色方法に関する。
The present invention relates to a novel dye decolorizing microorganism and a method for decolorizing a dye using the microorganism.

【0002】[0002]

【従来の技術】染色等により着色した廃水の脱色法とし
ては、凝集沈殿、オゾン酸化、活性炭吸着、次亜塩素酸
酸化、電解酸化などの物理・化学的脱色方法の検討が多
くなされてきた。排水の着色度は従来より問題視されて
きたが、平成3年10月、和歌山市で色抜き条例が制定
されて以来、特に注目されるようになった。本条例は平
成6年4月施行されたが、上記の方法は何れも処理コス
トの点で対応しうる技術ではなく、同年7月には規制値
が緩和された。その後和歌山市以外に規制は拡大してい
ないが、処理コスト、スペース、安定性が実用レベルを
超える技術が開発されれば、一気に規制が広がると考え
られている。
2. Description of the Related Art As a method for decolorizing wastewater colored by dyeing or the like, many studies have been made on physical and chemical decolorization methods such as coagulation sedimentation, ozone oxidation, activated carbon adsorption, hypochlorous acid oxidation, and electrolytic oxidation. Although the degree of coloration of wastewater has been regarded as a problem, it has been receiving special attention since the Wakayama City enacted a color removal ordinance in October 1991. This ordinance came into effect in April 1994, but none of the above methods was a technology that could be handled in terms of processing costs, and the regulation values were relaxed in July of the same year. Since then, regulations have not expanded beyond Wakayama City, but it is thought that regulations will expand at a stretch if technologies that have processing costs, space, and stability that exceed practical levels are developed.

【0003】生物法は一般に穏和な条件で脱色反応が進
み、物理化学的方法と比較して二次的な間題が少なく、
またコストの点でも有利と考えられていることから、こ
れまでにも活発な研究がなされ、多くの脱色能を有する
微生物が提供されている。例を挙げれば、シユードモナ
ス属細菌(微工研菌寄第1283号)による塩基性染料
の分解(特開昭48−82662号公報)、ノカルディ
ア属細菌(ATCC19070、19071)によるベ
ンゼン環含有染料の分解(特開昭48−56881号公
報)、アルカリゲネス属細菌(微工研菌寄第9183
号)による、アルカリ条件下でのモノアゾ系、ジアゾ
系、トリフェニルメタン系、メチン系、モノアゾポリマ
ー系染料の脱色(特開昭63−216472号公報)、
ミロセシウム属糸状菌(微工研菌寄第10728号)に
よるフタロシアニンの分解・脱色(特開平3−1669
8号公報)、バチルス属(微工研菌寄第13118
号)、キサントモナス属(微工研菌寄第13119
号)、アクロモバクター属(微工研菌寄第13120
号)各細菌によるアゾ系染料着色液の色消去もしくは低
減(特開平8−261号公報)、ゲオトリクム属糸状菌
(微工研菌寄第15348号)による染料の分解・脱色
(特開平9−173051号公報)、などがある。
[0003] In the biological method, the decolorization reaction generally proceeds under mild conditions, and there are few secondary problems as compared with the physicochemical method.
Also, since it is considered to be advantageous in terms of cost, active research has been made so far, and many microorganisms having decolorizing ability have been provided. Examples include decomposition of basic dyes by Pseudomonas spp. Bacteria (No. 1283), and benzene ring-containing dyes by Nocardia spp. Bacteria (ATCC 19070, 19071). Degradation (JP-A-48-56881), a bacterium belonging to the genus Alcaligenes (No.
Decolorization of monoazo, diazo, triphenylmethane, methine and monoazo polymer dyes under alkaline conditions (JP-A-63-216472).
Degradation and decolorization of phthalocyanine by filamentous fungi belonging to the genus Myrocesium (No. 10728).
No. 8), Bacillus sp.
No. 13), Xanthomonas sp.
No. 13), Achromobacter sp.
No.) Color elimination or reduction of azo dye coloring liquid by each bacterium (Japanese Patent Application Laid-Open No. 8-261), decomposition and decolorization of dye by a fungus of the genus Geotricum (No. 15348). No. 173051) and the like.

【0004】一方、染料は多種類あり、被染色素材など
に応じてそれぞれ使用されているが、使用量の多いもの
としては、主にポリエステルの染色に用いられる分散染
料と、綿などの染色に用いられる反応性染料が挙げられ
る。特に反応性染料は水溶性であり、排水の着色成分と
して問題となっている。また染料の化学構造の基本骨格
から、主にアゾ系とアントラキノン系があり、アゾ系染
料のほうが多く用いられている。従って、廃水の着色で
最も問題となる染料はアゾ系反応性染料と言うことがで
きる。
On the other hand, there are various types of dyes, which are used in accordance with the material to be dyed. However, those used in large amounts include disperse dyes mainly used for dyeing polyester and dyes for cotton and the like. The reactive dyes used are mentioned. In particular, reactive dyes are water-soluble and pose a problem as a coloring component of wastewater. Further, from the basic skeleton of the chemical structure of the dye, there are mainly an azo type and an anthraquinone type, and the azo type dye is used more frequently. Therefore, the most problematic dye for coloring wastewater can be called an azo-based reactive dye.

【0005】反応性染料による染色は染料種により異な
るが、通常高温(40〜80℃)、高アルカリ(pH
10〜11)で行われる。従って染色終了後の廃水は、
温度は若干低下するが、中高温・高アルカリである。こ
の様な廃水が直接処理できれば、中和・冷却を必要とせ
ず、コスト低減、効率化が期待できるが、この条件下で
脱色しうる微生物はこれまでに知られていない。
[0005] Dyeing with a reactive dye varies depending on the type of dye.
10-11). Therefore, wastewater after dyeing is completed
Although the temperature drops slightly, it is a medium to high temperature and high alkali. If such wastewater can be directly treated, neutralization and cooling are not required, and cost reduction and efficiency can be expected. However, microorganisms that can decolorize under this condition have not been known so far.

【0006】[0006]

【発明が解決しようとする課題】本発明が解決しようと
する課題は効率的に微生物によって染料の脱色方法を提
供することにある。さらには使用量が多く、廃水の着色
源として最も問題となるアゾ系反応性染料を、染色直後
の高温・高アルカリ条件下で脱色することが可能な微生
物、およびこれを用いた効率よい脱色方法を提供するこ
とにある。
SUMMARY OF THE INVENTION An object of the present invention is to provide a method for efficiently decolorizing a dye by a microorganism. Furthermore, microorganisms that can decolor azo-based reactive dyes, which are the most problematic as a coloring source of wastewater, under high temperature and high alkali conditions immediately after dyeing, and an efficient decolorization method using this Is to provide.

【0007】[0007]

【課題を解決するための手段】本発明は、バチルス属に
属し、アルカリ条件および/または40℃以上の温度で
染料の脱色能力を有する微生物、および該微生物を用い
た染料の脱色方法である。
SUMMARY OF THE INVENTION The present invention relates to a microorganism belonging to the genus Bacillus and capable of decolorizing a dye under alkaline conditions and / or a temperature of 40 ° C. or higher, and a method for decolorizing a dye using the microorganism.

【0008】[0008]

【発明の実施の形態】本発明の微生物は、バチルス属に
属するものであり、アルカリ条件(特にpH9以上)お
よび/または40℃以上の温度で染料を脱色する能力を
有するものである。
BEST MODE FOR CARRYING OUT THE INVENTION The microorganism of the present invention belongs to the genus Bacillus and has the ability to decolorize a dye under alkaline conditions (particularly pH 9 or more) and / or a temperature of 40 ° C. or more.

【0009】本発明の微生物は以下のようにして取得さ
れた。全国各地の土壌、堆肥、活性汚泥等のサンプル
を、アゾ系反応性染料であるリアクティブブラック5を
0.025%、ペプトンを0.5%、酵母エキスを0.
2%、リン酸2カリウムを0.1%、硫酸マグネシウム
・7水和物を0.02%、炭酸ナトリウムを1%を含む
寒天培地(pH 10.5)に加え、45℃で培養し
た。1〜2日後青色の培地中にオレンジ色のクリアーゾ
ーンを形成する微生物を分離し、純化を繰り返して、1
種の細菌株を単離した。本菌株は上記と同じ培地で30
℃で培養した場合や、炭酸ナトリウムを添加しない培地
(pH 7.4)で30℃もしくは45℃で培養した場
合は、3日後でもクリアーゾーンは形成されなかった。
[0009] The microorganism of the present invention was obtained as follows. Samples of soil, compost, activated sludge, etc. from various parts of the country were analyzed using reactive black 5, which is an azo-based reactive dye, at 0.025%, peptone at 0.5%, and yeast extract at 0.1%.
An agar medium (pH 10.5) containing 2%, 0.1% dipotassium phosphate, 0.02% magnesium sulfate heptahydrate, and 1% sodium carbonate was added and cultured at 45 ° C. After 1-2 days, microorganisms forming an orange clear zone in a blue medium are separated, and purification is repeated.
Bacterial strains of the species were isolated. This strain is 30 times in the same medium as above.
When cultured at 30 ° C or 45 ° C in a medium (pH 7.4) without the addition of sodium carbonate, no clear zone was formed even after 3 days.

【0010】以下に本菌株の菌学的性質を示す。 (a) 形態的性質 (1) 細胞の形、大きさ 桿菌(0.8 x 4 μm) (2) 運動性(鞭毛) 有(周鞭毛) (3) 胞子 有(球状) (4) 胞子嚢 一末端が膨らんでいるThe bacteriological properties of the present strain are shown below. (a) Morphological properties (1) Cell shape and size Bacillus (0.8 x 4 μm) (2) Motility (flagellate) Yes (perioflagellate) (3) Spore Yes (spherical) (4) Spore sac One end is bulging

【0011】(b) 培養的性質(pH 10.3で試験) (1) 肉汁寒天平板培養 コロニーは中程度の大き
さ、凸状、表面は平滑、周縁はギザギザ、黄みがかった
白色、不透明 (2) 肉汁液体培養 若干の濁り (3) 肉汁ゼラチン穿刺培養 液化する
(B) Cultural properties (tested at pH 10.3) (1) Broth agar plate culture The colonies are medium in size, convex, smooth in surface, jagged at the periphery, yellowish white, opaque (2) Broth liquid culture Slight turbidity (3) Broth gelatin puncture culture Liquefaction

【0012】 (c) 生理学的性質 (1) グラム染色性 + (2) 硝酸塩の還元 + (3) 脱窒反応 − (4) VPテスト + (5) インドールの生成 − (6) 硫化水素の生成 − (7) デンプンの加水分解 + (8) カゼインの加水分解 + (9) クエン酸の利用 +(シモンズ、クリステン
セン培地とも) (10) 無機窒素源 +(アンモニア態、硝酸態
とも) (11) 色素の生成 − (12) ウレアーゼ + (13) オキシダーゼ +(弱い) (14) カタラーゼ + (15) 生育の範囲 25℃〜60℃で生育(至
適温度は45℃)pH 7.5〜12.0で生育(至適
pHは9〜10) (16) NaClの影響 10%存在下で生育 (17) 酸素に対する態度 通性嫌気性 (18) O/Fテスト O/F (19) L−アラビノース、D−キシロース、 D−グルコ
ース、D−マンノース、 D−フラクトース、 D−ガラ
クトース、マルトース、シュークロース、ラクトース、
トレハロース、D−マンニトール、デンプンから酸を生
成するがガスは生成しない。D−ソルビトール、イノシ
トール、グリセンリンからは酸もガスも生成しない。 (20) 栄養要求性 なし
(C) Physiological properties (1) Gram stainability + (2) Reduction of nitrate + (3) Denitrification reaction-(4) VP test + (5) Formation of indole-(6) Formation of hydrogen sulfide − (7) Hydrolysis of starch + (8) Hydrolysis of casein + (9) Use of citric acid + (both Simmons and Christensen media) (10) Inorganic nitrogen source + (both ammonia and nitrate) (11) Formation of pigment-(12) Urease + (13) Oxidase + (weak) (14) Catalase + (15) Growth range Growth at 25 ° C to 60 ° C (optimum temperature is 45 ° C) pH 7.5 to 12. Grow at 0 (optimal pH is 9 to 10) (16) Effect of NaCl Grow in the presence of 10% (17) Attitude to oxygen Facultative anaerobic (18) O / F test O / F (19) L-arabinose , D-xylose, D-glucose, D-mannose, D-fructose, D-galactose, mal Over vinegar, sucrose, lactose,
It produces acid but not gas from trehalose, D-mannitol and starch. D-sorbitol, inositol and glycerin do not produce any acid or gas. (20) Nutrition requirements None

【0013】以上の結果をバージェイズ・マニュアル・
オブ・システマティック・バクテリオロジーに照らし合
わせた。本菌株はグラム陽性、桿菌で、カタラーゼおよ
びオキシダーゼ陽性、運動性を有し、胞子を形成するこ
とからバチルス属に属する細菌であることは明らかで、
通性嫌気性、胞子の形、膨らみの位置、各種糖の資化
性、食塩濃度耐性等の点で、類似の種はなく、さらに生
育pHから新種の好アルカリ性バチルスであり、バチル
ス sp. DA1(生命工研菌寄第16921号)と命名し
た。
[0013] The above results can be obtained by
Of the systematic bacteriology. This strain is Gram-positive, bacillus, catalase and oxidase-positive, has motility, and is a bacterium belonging to the genus Bacillus because it forms spores.
There is no similar species in facultative anaerobic, spore shape, swelling position, assimilation of various sugars, salt concentration tolerance, etc. (Biotechnological Laboratory No. 16921).

【0014】本新菌種は、バチルス属に属する他の菌種
と下記の点で菌学的性質を異にする。本新菌種に最も近
縁な種は、Bacillus pasteurii であるが、VPテスト、
デンプンの加水分解性、55℃での生育において異なる。
次に近いのが、Bacillus licheniformis であるが、胞
子の形状、胞子嚢の膨らみ、pH 6.8以下での生育におい
て異なる。Bacillus coagulrans は、55℃での生育+だ
が、胞子の形状、ゼラチンの液化、pH 6.8以下での生
育、食塩濃度耐性が異なる。Bacillus circulansは、胞
子の形状、VPテスト、pH 6.8以下での生育、食塩濃度耐
性、55℃での生育が異なる。さらにBacillus brevis
は、胞子の形状、嫌気下での生育、糖から酸の生成、VP
テスト、pH 6.8以下での生育、食塩濃度耐性が異なる。
The new strain differs from other strains belonging to the genus Bacillus in the following points in bacteriological properties. The most closely related species to this new strain is Bacillus pasteurii.
Different in starch hydrolyzability, growth at 55 ° C.
The next closest is Bacillus licheniformis, which differs in spore shape, spore swelling, and growth below pH 6.8. Bacillus coagulrans grow + at 55 ° C, but differ in spore morphology, liquefaction of gelatin, growth below pH 6.8, and salt concentration tolerance. Bacillus circulans differ in spore morphology, VP test, growth below pH 6.8, salt concentration tolerance, and growth at 55 ° C. Bacillus brevis
Indicates the spore shape, growth under anaerobic conditions, generation of acid from sugar, VP
Tests, growth at pH 6.8 or lower, salt concentration tolerance are different.

【0015】本発明を実施するに際しては、本菌を染料
含有溶液に直接接種しても良く、またあらかじめ培養し
た菌体を染料含有溶液に添加しても良い。培養に際して
は特に限定はしないが、各種グルコースをはじめとする
各種炭素源、タンパク質、ペプトン、酵母エキス、アミ
ノ酸等の炭窒素源、硫酸アンモニウム、硝酸ナトリウ
ム、硫酸マグネシウム、硫酸第1鉄などの各種無機塩類
等を添加した培地を用いることができる。培養における
pHや温度条件は上述の通りである。また好気、嫌気何
れの場合でも良いが、好気条件のほうが増殖速度が高
い。
In practicing the present invention, the present bacterium may be directly inoculated into a dye-containing solution, or cells previously cultured may be added to the dye-containing solution. The cultivation is not particularly limited, but various carbon sources such as various glucoses, carbon sources such as proteins, peptones, yeast extracts, and amino acids, and various inorganic salts such as ammonium sulfate, sodium nitrate, magnesium sulfate, and ferrous sulfate. And the like can be used. The pH and temperature conditions in the culture are as described above. Either aerobic or anaerobic may be used, but the growth rate is higher under aerobic conditions.

【0016】本発明を用いて脱色処理するときの温度
は、特に限定されるものではないが、40℃以上、60
℃以下が好ましい。至適処理速度での利用や雑菌汚染の
防止を考慮すると40〜55℃がより好ましい。またp
Hに関しては、pH 7.5以上、pH 11.0以下が
好ましく、さらにはpH 8.5以上、pH 10.5以
下がより好ましい。
The temperature for the decolorization treatment using the present invention is not particularly limited.
C. or less is preferred. Considering utilization at an optimum treatment rate and prevention of contamination by various bacteria, 40 to 55 ° C is more preferable. Also p
Regarding H, the pH is preferably 7.5 or more and 11.0 or less, and more preferably 8.5 or more and 10.5 or less.

【0017】被処理物は、特に限定しないが、本菌によ
り脱色される染料を含有する水溶液、工場廃水、下水等
が挙げられる。本菌が特にアルカリ、中高温条件で脱色
能を有することを考慮すると、同条件で染色を行う反応
性染料による染色廃液の脱色に顕著な効果をもたらす。
The material to be treated is not particularly limited, and examples thereof include an aqueous solution containing a dye that is decolorized by the fungus, factory wastewater, and sewage. Considering that the bacterium has a decolorizing ability particularly under alkaline, medium and high temperature conditions, it has a remarkable effect on the decolorization of the dyeing waste liquid by the reactive dye which is dyed under the same conditions.

【0018】本菌株は通性嫌気性であるが、好気条件で
は脱色せず、また完全な嫌気条件でも脱色速度がやや落
ちる。従って、適度の嫌気状態で行うのが最も好まし
く、好気条件のように酸素を供給する必要がないので、
経済的に有利である。
Although this strain is facultatively anaerobic, it does not decolorize under aerobic conditions, and its decolorization speed is slightly reduced even under completely anaerobic conditions. Therefore, it is most preferable to perform the reaction in a moderately anaerobic state, and it is not necessary to supply oxygen as in the aerobic condition.
Economically advantageous.

【0019】以下に実施例を挙げて本発明を具体的に説
明する。
Hereinafter, the present invention will be described specifically with reference to examples.

【0020】[0020]

【実施例】[実施例1]ペプトンを0.5%、酵母エキ
スを0.2%、リン酸2カリウムを0.1%、硫酸マグ
ネシウム・7水和物を0.02%、炭酸ナトリウムを1
%含む基本培地にリアクティブブラック5を0.025
%、寒天を1.5%加えた固体培地(pH 10.5)
を作製し、その表面上にバチルス sp. DA1の菌体懸濁液
を微量滴下し、45℃で培養した。1日後濃紺の培地の
中で、菌体懸濁液を滴下したところを中心にオレンジ色
のクリアーゾーン(反対側か透けて見える)が形成され
た。
[Example 1] Peptone 0.5%, yeast extract 0.2%, dipotassium phosphate 0.1%, magnesium sulfate heptahydrate 0.02%, sodium carbonate 1
% Of reactive black 5 in a basic medium containing 0.025%
%, Solid medium supplemented with 1.5% agar (pH 10.5)
Was prepared, and a microbial cell suspension of Bacillus sp. DA1 was dripped on the surface thereof and cultured at 45 ° C. One day later, in the dark blue medium, an orange clear zone (visible on the opposite side or see through) was formed around the point where the cell suspension was dropped.

【0021】[実施例2]可溶性デンプンを1%、ペプ
トンを0.5%、酵母エキスを0.5%、リン酸2カリ
ウムを0.1%、硫酸マグネシウム・7水和物を0.0
2%、炭酸ナトリウムを1%含む液体培地にバチルス s
p. DA1を接種し、45℃で1晩好気的に培養した。この
培養液15mlを遠心分離して得た菌体を、各種染料を
0.025%加えた基本培地(実施例1に記載)に懸濁
し、45℃で静置した。またそれぞれの染料含有培地に
ついて、菌体を加えない場合を対照とした。8時間後の
遠心分離上清液について各染料の最大吸収波長における
吸収を測定し、対照に対し減少した値を、対照を100
とする脱色率で表した。結果を表1にまとめた。なお分
散染料(表中のDisperse yellow 3とDisperse blue 3)
はアセトンを最終濃度が50%となるよう添加して遠心
分離上清液を調製した。
Example 2 1% soluble starch, 0.5% peptone, 0.5% yeast extract, 0.1% dipotassium phosphate, 0.0% magnesium sulfate heptahydrate
Bacillus s in a liquid medium containing 2% and 1% sodium carbonate
p. DA1 was inoculated and cultured aerobically at 45 ° C. overnight. The cells obtained by centrifuging 15 ml of this culture were suspended in a basic medium (described in Example 1) containing 0.025% of various dyes, and allowed to stand at 45 ° C. In each dye-containing medium, the case where no cells were added was used as a control. Eight hours later, the supernatant at the maximum absorption wavelength of each centrifuged supernatant was measured for the centrifuged supernatant.
The decolorization rate was expressed as follows. The results are summarized in Table 1. Disperse dyes (Disperse yellow 3 and Disperse blue 3 in the table)
Acetone was added to a final concentration of 50% to prepare a centrifuged supernatant.

【0022】[0022]

【表1】 [Table 1]

【0023】[0023]

【発明の効果】新規微生物を利用することにより、中高
温、アルカリ条件下で、染料により着色した溶液の着色
度を低減することが可能となった。特に反応性染料を高
温、高アルカリ条件で用いる染色の廃水処理に顕著な効
果をもたらす。
The use of the novel microorganisms has made it possible to reduce the degree of coloring of a solution colored with a dye under a medium-high-temperature, alkaline condition. In particular, it has a remarkable effect on wastewater treatment of dyeing using a reactive dye under high temperature and high alkali conditions.

───────────────────────────────────────────────────── フロントページの続き Fターム(参考) 4B065 AA15X AC12 AC20 BA21 BA23 BB01 BB03 BB18 BB24 BB29 BC01 BC02 BC03 BC05 BD15 BD50 CA56 4H057 AA02 GA90 HA01 HA06 4L031 BA13 BA14 BA17 BA18 BA39 CA01 DA00 DA09  ──────────────────────────────────────────────────続 き Continued on the front page F term (reference) 4B065 AA15X AC12 AC20 BA21 BA23 BB01 BB03 BB18 BB24 BB29 BC01 BC02 BC03 BC05 BD15 BD50 CA56 4H057 AA02 GA90 HA01 HA06 4L031 BA13 BA14 BA17 BA18 BA39 CA01 DA00 DA09

Claims (10)

【特許請求の範囲】[Claims] 【請求項1】 バチルス属に属し、アルカリ条件で染料
の脱色能力を有する新規微生物。
1. A novel microorganism belonging to the genus Bacillus and capable of decolorizing a dye under alkaline conditions.
【請求項2】 バチルス属に属し、40℃以上の温度で
染料の脱色能力を有する新規微生物。
2. A novel microorganism belonging to the genus Bacillus and capable of decolorizing a dye at a temperature of 40 ° C. or higher.
【請求項3】 バチルス属に属し、アルカリ条件でかつ
40℃以上の温度で反応性染料の脱色能力を有する新規
微生物。
3. A novel microorganism belonging to the genus Bacillus and having a decolorizing ability of a reactive dye under alkaline conditions and at a temperature of 40 ° C. or higher.
【請求項4】 バチルス属に属し、通性嫌気性、胞子の
形、膨らみの位置、各種糖の資化性および食塩濃度耐性
において他の菌種と菌学的性質を異にする新菌種バチル
ス sp. DAI。
4. A new strain belonging to the genus Bacillus which differs from other strains in mycological properties in facultative anaerobic, spore form, swelling position, assimilation of various sugars and salt concentration tolerance. Bacillus sp. DAI.
【請求項5】 染料の脱色能を有する生命工研菌寄第1
6921号として寄託されたバチルス sp. DA1株。
5. A biotechnological laboratory having the ability to decolorize dyes.
Bacillus sp. Strain DA1 deposited as No. 6921.
【請求項6】 請求項1記載の微生物を用い、アルカリ
条件で処理することを特徴とする染料の脱色方法。
6. A method for decolorizing a dye, comprising treating the microorganism according to claim 1 under alkaline conditions.
【請求項7】 請求項2記載の微生物を用い、40℃以
上で処理することを特徴とする染料の脱色方法。
7. A method for decolorizing a dye, comprising treating the microorganism according to claim 2 at 40 ° C. or higher.
【請求項8】 請求項3記載の微生物を用い、アルカリ
条件下40℃以上で処理することを特徴とする染料の脱
色方法。
8. A method for decolorizing a dye, comprising treating the microorganism according to claim 3 at 40 ° C. or higher under alkaline conditions.
【請求項9】 新菌種バチルス sp. DAI を用いること
を特徴とする染料の脱色方法。
9. A method for decolorizing a dye, comprising using a new strain of Bacillus sp. DAI.
【請求項10】 新菌種バチルス sp. DAI が生命工菌
寄第16921号として寄託されたバチルス sp. DAI株
である請求項9記載の脱色方法。
10. The decolorizing method according to claim 9, wherein the new strain Bacillus sp. DAI is a Bacillus sp. DAI strain deposited as Seiko No. 16921.
JP27029098A 1998-09-24 1998-09-24 Novel microorganism and method for decoloring dye using the same Expired - Fee Related JP3846062B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP27029098A JP3846062B2 (en) 1998-09-24 1998-09-24 Novel microorganism and method for decoloring dye using the same

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP27029098A JP3846062B2 (en) 1998-09-24 1998-09-24 Novel microorganism and method for decoloring dye using the same

Publications (2)

Publication Number Publication Date
JP2000093164A true JP2000093164A (en) 2000-04-04
JP3846062B2 JP3846062B2 (en) 2006-11-15

Family

ID=17484212

Family Applications (1)

Application Number Title Priority Date Filing Date
JP27029098A Expired - Fee Related JP3846062B2 (en) 1998-09-24 1998-09-24 Novel microorganism and method for decoloring dye using the same

Country Status (1)

Country Link
JP (1) JP3846062B2 (en)

Cited By (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2004082107A (en) * 2002-06-24 2004-03-18 Kuraray Co Ltd Equipment and method for treating waste water containing nitrogen-containing dyestuff
JP2004267127A (en) * 2003-03-10 2004-09-30 Kobelco Eco-Solutions Co Ltd New microorganism and method for treating organic solid material by using the same microorganism
KR100457071B1 (en) * 2001-04-07 2004-11-10 주식회사 생명탄 Development of decolorization and biodegradation techniques for dyeing waste waters treatment by bacterial consortium
CN1325398C (en) * 2003-06-25 2007-07-11 中国石油化工股份有限公司 Biochemical treatment process for recovered waste water in oil field
JP4536158B1 (en) * 2010-04-15 2010-09-01 三木理研工業株式会社 Colored wastewater treatment method and colored wastewater treatment apparatus used in the method
CN112374704A (en) * 2020-12-01 2021-02-19 江苏南资环保科技有限公司 Biological decolorization process for pesticide wastewater

Cited By (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR100457071B1 (en) * 2001-04-07 2004-11-10 주식회사 생명탄 Development of decolorization and biodegradation techniques for dyeing waste waters treatment by bacterial consortium
JP2004082107A (en) * 2002-06-24 2004-03-18 Kuraray Co Ltd Equipment and method for treating waste water containing nitrogen-containing dyestuff
JP4663218B2 (en) * 2002-06-24 2011-04-06 株式会社クラレ Waste water treatment apparatus and treatment method containing nitrogen-containing dye
JP2004267127A (en) * 2003-03-10 2004-09-30 Kobelco Eco-Solutions Co Ltd New microorganism and method for treating organic solid material by using the same microorganism
CN1325398C (en) * 2003-06-25 2007-07-11 中国石油化工股份有限公司 Biochemical treatment process for recovered waste water in oil field
JP4536158B1 (en) * 2010-04-15 2010-09-01 三木理研工業株式会社 Colored wastewater treatment method and colored wastewater treatment apparatus used in the method
JP2011224415A (en) * 2010-04-15 2011-11-10 Miki Riken Kogyo Kk Colored waste water treatment method and colored waste water treatment apparatus used for the method
CN112374704A (en) * 2020-12-01 2021-02-19 江苏南资环保科技有限公司 Biological decolorization process for pesticide wastewater

Also Published As

Publication number Publication date
JP3846062B2 (en) 2006-11-15

Similar Documents

Publication Publication Date Title
Dias et al. Microbial ecology of activated sludge: I. Dominant bacteria
Watanabe et al. Growth and flocculation of a marine photosynthetic bacterium Rhodovulum sp.
CA1318871C (en) Method for producing 2-keto-l-gulonic acid
Ohmomo et al. Screening of anaerobic bacteria with the ability to decolorize molasses melanoidin
Taskin et al. Reactive dye bioaccumulation by fungus Aspergillus niger isolated from the effluent of sugar fabric-contaminated soil
DE2413963C3 (en) Process for the production of 2-keto-L-gulonic acid and its salts by microbiological means
Sugiura et al. Isolation of azo-dye-degrading microorganisms and their application to white discharge printing of fabric
US3930947A (en) Method of producing microbial cells from methane
AU615661B2 (en) Acid urease and production thereof
JP2000093164A (en) New microorganism and dye decoloration using the same
Prasertsan et al. Isolation, identification and growth conditions of photosynthetic bacteria found in seafood processing wastewater
CA1040565A (en) D-ribose production by bacillus
FI86557C (en) FOERFARANDE FOER FRAMSTAELLNING AV ALFAAMYLAS MEDELST EN MICROORGANISM AV ARTEN BACILLUS SUBTILIS.
US4721676A (en) Novel thermophile isolate having thermostable hydrolytic activity
JP2998055B2 (en) A method and apparatus for decolorizing colored wastewater containing an azo dye.
WATANABE et al. NEW POLYENIC ANTIBIOTICS ACTIVE AGAINST GRAM-POSITIVE AND-NEGATIVE BACTERIA II. SCREENING OF ANTIBIOTIC PRODUCERS AND TAXONOMICAL PROPERTIES OF GLUCONOBACTER SP. W-315
JP2001078760A (en) Depigmenting bacillus-immobilizing carrier
Kawai et al. Bacterial assimilation of polytetramethylene glycol
Kakii et al. Isolation and characterization of a Ca++-dependent floc-forming bacterium
US4572898A (en) Thermophile isolate having thermostable hydrolytic activity
US3740318A (en) Composition of matter and process
US3896000A (en) Halophilic nuclease and a process for producing the same
US5480781A (en) Bacillus strains for oxidizing hydroxy groups of cholic acid and cheno deoxycholic acid to keto groups
KR0183318B1 (en) Wastewater treatment method using bacillus sp. micro organism
Shah Microbial decolorization of reactive azo dyes by Bacillus spp. ETL-1949 under anaerobic condition

Legal Events

Date Code Title Description
A131 Notification of reasons for refusal

Free format text: JAPANESE INTERMEDIATE CODE: A131

Effective date: 20060404

A521 Written amendment

Free format text: JAPANESE INTERMEDIATE CODE: A523

Effective date: 20060601

TRDD Decision of grant or rejection written
A01 Written decision to grant a patent or to grant a registration (utility model)

Free format text: JAPANESE INTERMEDIATE CODE: A01

Effective date: 20060801

A61 First payment of annual fees (during grant procedure)

Free format text: JAPANESE INTERMEDIATE CODE: A61

Effective date: 20060814

LAPS Cancellation because of no payment of annual fees