JPH0441594B2 - - Google Patents

Info

Publication number
JPH0441594B2
JPH0441594B2 JP26064788A JP26064788A JPH0441594B2 JP H0441594 B2 JPH0441594 B2 JP H0441594B2 JP 26064788 A JP26064788 A JP 26064788A JP 26064788 A JP26064788 A JP 26064788A JP H0441594 B2 JPH0441594 B2 JP H0441594B2
Authority
JP
Japan
Prior art keywords
ethanolamines
triethanolamine
bacterium
negative
growth
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Expired
Application number
JP26064788A
Other languages
Japanese (ja)
Other versions
JPH02109975A (en
Inventor
Satoshi Imashiro
Yasuyuki Maki
Seiichi Kaneko
Yoshihiro Sato
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.)
Kanagawa Prefecture
Original Assignee
Kanagawa Prefecture
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 Kanagawa Prefecture filed Critical Kanagawa Prefecture
Priority to JP26064788A priority Critical patent/JPH02109975A/en
Publication of JPH02109975A publication Critical patent/JPH02109975A/en
Publication of JPH0441594B2 publication Critical patent/JPH0441594B2/ja
Granted legal-status Critical Current

Links

Description

【発明の詳細な説明】[Detailed description of the invention]

[産業上の利用分野] 本発明はエタノールアミン類を分解するフラボ
バクテリウム・アクアタイルに関する。 エタノールアミン類は防錆剤として切削油剤に
利用される。切削油剤中におけるエタノールアミ
ン類の含有量は様々であるが、40%に達する場合
もある。 [従来の技術、発明が解決しようとする課題] 切削油廃液を処理する方法として擬集法、活性
汚泥法、活性炭吸着法などが知られているが、こ
れらの方法では該廃液中のエタノールアミン類、
特にトリエタノールアミン、ジエタノールアミン
は離分解性であるため、除去することができな
い。 しかも、エタノールアミン類は生体系への安全
性が疑問視され、水溶性であるため、一旦自然環
境に出ると、拡散も大きく、環境汚染を起こし、
自然浄化は困難である。そのため、未処理のまま
廃棄することには重大な問題がある。 [課題を解決するための手段] そこで、本発明者らは微生物を利用してエタノ
ールアミン類を分解すべく、微生物の検索を行つ
たところ、横浜市金沢区内の土壌から分離した微
生物がトリエタノールアミンとジエタノールアミ
ンを効率よく分解することを見出し、本発明に到
達した。 すなわち本発明は、エタノールアミン類を分解
するフラボバクテリウム・アクアタイル
(Flavobacterium aquatile)に関する。 本菌は、上記した如く、横浜市金沢区内の土壌
からトリエタノールアミンを単独炭素源とする分
離培地を用いて単離されたものであり、以下のよ
うな菌学的性質を有している。 A 形態学的性質 (1) 細胞の形および大きさ:桿菌 0.6×2.0μ (2) 細胞の多形性:なし (3) 運動性:なし (4) 胞子:形成しない (5) グラム染色性:陰性 (6) 抗酸性:なし B 各培地における生育状態 (1) 標準寒天培地(30℃、5日間) 生育は良好、形状は円形、表面隆起は扁平
上、表面は円滑、色調は黄色 (2) トリプトソイ斜面培地 生育は適度、表面は円滑、色調は淡黄色 (3) トリエタノールアミン寒天培地(トリエタ
ノールアミン1%含有) 生育は適度、形状は円形、表面隆起は扁平
状、表面は円滑、色調は淡黄色 (4) ハートインフユージヨン寒天培地 生育は良好、形状は円形、色調は黄色 C 生理学的性質 (1) 硝酸塩の還元:還元する (2) インドールの生成:陰性 (3) 硫化水素の生成:陰性 (4) デンプンの加水分解:陽性 (5) クエン酸の利用:クリステンゼン培地、シ
モンズ培地では利用しない (6) リジン脱炭酸:陰性 (7) エスクリンの加水分解:陰性 (8) カゼインの加水分解:陽性 (9) 尿素分解:陰性 (10) カタラーゼ:陽性 (11) オキシラーゼ:陽性 (12) OF試験:酸化型 (13) 色素の生成:非水溶性黄色色素を生成 (14) 生育の範囲:温度15〜30℃ (15) 酸素要求性:好気性 (16) 塩化ナトリウム要求性:陰性 (17) β−ガラクトシダーゼ(ONPG):陰性 (18) 糖類から酸の生成
[Industrial Application Field] The present invention relates to Flavobacterium aquatile which decomposes ethanolamines. Ethanolamines are used in cutting fluids as rust preventive agents. The content of ethanolamines in cutting fluids varies, but can reach up to 40%. [Prior Art and Problems to be Solved by the Invention] Known methods for treating cutting oil waste include the aggregation method, activated sludge method, and activated carbon adsorption method. kind,
In particular, triethanolamine and diethanolamine cannot be removed because they are separable. Moreover, the safety of ethanolamines to biological systems is questionable, and since they are water-soluble, once they are released into the natural environment, they diffuse widely and cause environmental pollution.
Natural purification is difficult. Therefore, there is a serious problem in disposing of it untreated. [Means for Solving the Problems] Therefore, the present inventors conducted a search for microorganisms in order to decompose ethanolamines using microorganisms, and found that microorganisms isolated from soil in Kanazawa Ward, Yokohama City were found to be trivial. The present invention was achieved by discovering that ethanolamine and diethanolamine can be efficiently decomposed. That is, the present invention relates to Flavobacterium aquatile that decomposes ethanolamines. As mentioned above, this bacterium was isolated from soil in Kanazawa Ward, Yokohama City using an isolation medium containing triethanolamine as the sole carbon source, and has the following mycological properties. There is. A Morphological properties (1) Cell shape and size: Bacillus 0.6×2.0μ (2) Cell pleomorphism: None (3) Motility: None (4) Spores: Not formed (5) Gram staining : Negative (6) Anti-acidity: None B Growth status in each medium (1) Standard agar medium (30℃, 5 days) Good growth, circular shape, flat surface ridges, smooth surface, yellow color ( 2) Trypto soy slant medium Growth is moderate, surface is smooth, color is pale yellow (3) Triethanolamine agar medium (contains 1% triethanolamine) Growth is moderate, shape is circular, surface ridges are flat, surface is smooth , pale yellow in color (4) Heart infusion agar medium Good growth, circular in shape, yellow in color C Physiological properties (1) Reduction of nitrate: Reducing (2) Formation of indole: Negative (3) Sulfidation Hydrogen generation: Negative (4) Starch hydrolysis: Positive (5) Citric acid usage: Not used in Christensen medium or Simmons medium (6) Lysine decarboxylation: Negative (7) Aesculin hydrolysis: Negative (8 ) Casein hydrolysis: Positive (9) Urea decomposition: Negative (10) Catalase: Positive (11) Oxirase: Positive (12) OF test: Oxidized type (13) Pigment production: Produces water-insoluble yellow pigment (14 ) Growth range: Temperature 15-30℃ (15) Oxygen requirement: Aerobic (16) Sodium chloride requirement: Negative (17) β-galactosidase (ONPG): Negative (18) Production of acid from sugars

【表】 以上の諸性質をバージーズ・マニユアル・オ
ブ・システマテイツク・バクテリオロジー、第1
版(1984年)に基づいて検索したところ、本菌は
フラボバクテリウム・アクアタイルであると確認
された。しかし、既知の菌株にはエタノールアミ
ン類を分解する能力を有するものは知られていな
い。 本菌はフラボバクテリウム・アクアタイルKK
−111と命名され、工業技術院微生物工業技術研
究所にFERM P−10335として寄託されている。
本発明においては、本菌を自然にもしくは人工的
手段によつて変異させて得られる変異株であつて
もエタノールアミン類を分解する能力を有するも
のはすべて包含される。 次に、本菌によるエタノールアミン類の分解方
法としては、本菌をエタノールアミン類と接触さ
せればよく、特別な条件を必要としないが、通常
はエタノールアミン類のほかに硫酸アンモニウ
ム、リン酸カリウム、マグネシウム塩、鉄塩など
の窒素源、無機塩類などを含む系で接触させる。 培養は好気的条件下、PH6.0〜8.0、温度15〜35
℃、好ましくは25〜30℃でエタノールアミン類が
十分に資化されるまで行う。エタノールアミン類
の初濃度は0.01〜3%、好ましくは0.05〜1%と
すべきであり、このような条件下では5〜10日程
度の培養によつてエタノールアミン類を完全に分
解することができる。 なお、本菌によるエタノールアミン類、特にト
リエタノールアミンおよびジエタノールアミンの
分解の評価法として、エタノールアミン類を単独
炭素源とし、硫酸アンモニウム、リン酸二水素カ
リウム、硫酸マグネシウムおよび塩化第二鉄を含
む培地(PH6.0〜8.0)に本菌を接種し、25〜30℃
で振とう培養を行い、本菌の増殖状態、エタノー
ルアミン類の濃度および溶存総有機炭素量
(TOC)を経時的に測定する方法がある。トリエ
タノールアミンおよびジエタノールアミンについ
ては、初濃度を1%以下とすれば、比較的短期間
に効率よく分解することができる。 [実施例] 次に、本発明を実施例によつて詳しく説明す
る。 実施例 1 200ml容フラスコにトリエタノールアミン0.1
%、硫酸アンモニウム0.1%、リン酸二水素カリ
ウム0.2%、硫酸マグネシウム40ppmおよび塩化
第二鉄40ppmを含む培地(PH7.0)100mlを入れ、
常法により滅菌後、フラボバクテリウム・アクア
タイルKK−111(FERM P−10335)を植菌し、
30℃で振とう培養を行い、その増殖状態、トリエ
タノールアミンおよび溶存TOCの残存量を経時
的に測定した。結果を第1図に示す。 図から明らかなように、本菌の増殖に伴なつて
トリエタノールアミンと溶存TOCの減少が認め
られ、培養9日目にはトリエタノールアミンの分
解率は99.9%以上となり、また溶存TOCの除去
率も92%以上であつた。 実施例 2 実施例1において、トリエタノールアミンの代
りにジエタノールアミンを用いたこと以外は実施
例1と同様に行つた。その結果、培養6日目でジ
エタノールアミンの分解率は95%であつた。 [発明の効果] 本発明の微生物はエタノールアミン類を効率よ
く分解するので、該エタノールアミン類を含有す
る切削油廃液等を処理する場合に利用することが
できる。
[Table] The above properties are summarized in Birdsey's Manual of Systematic Bacteriology, Volume 1.
(1984), this bacterium was confirmed to be Flavobacterium aquatile. However, none of the known bacterial strains is known to have the ability to degrade ethanolamines. This bacterium is Flavobacterium aquatile KK
-111, and has been deposited as FERM P-10335 at the Institute of Microbial Technology, Agency of Industrial Science and Technology.
The present invention includes all mutant strains that have the ability to decompose ethanolamines, even if they are mutant strains obtained by mutating this bacterium naturally or by artificial means. Next, the method for decomposing ethanolamines by this bacterium is to bring the bacterium into contact with ethanolamines, and no special conditions are required. , a nitrogen source such as magnesium salt, iron salt, and inorganic salts. Cultivation is carried out under aerobic conditions, pH 6.0-8.0, temperature 15-35.
C., preferably 25 to 30.degree. C., until the ethanolamines are fully assimilated. The initial concentration of ethanolamines should be 0.01 to 3%, preferably 0.05 to 1%, and under these conditions, ethanolamines can be completely decomposed by culturing for about 5 to 10 days. can. In addition, as a method for evaluating the decomposition of ethanolamines, particularly triethanolamine and diethanolamine, by this bacterium, we used a medium containing ethanolamines as the sole carbon source and containing ammonium sulfate, potassium dihydrogen phosphate, magnesium sulfate, and ferric chloride ( Inoculate this bacteria at 25-30℃ (PH6.0-8.0).
There is a method in which the growth state of this bacterium, the concentration of ethanolamines, and the total amount of dissolved organic carbon (TOC) are measured over time by culturing with shaking. Triethanolamine and diethanolamine can be efficiently decomposed in a relatively short period of time if the initial concentration is 1% or less. [Example] Next, the present invention will be explained in detail with reference to an example. Example 1 Triethanolamine 0.1 in a 200ml flask
%, ammonium sulfate 0.1%, potassium dihydrogen phosphate 0.2%, magnesium sulfate 40ppm and ferric chloride 40ppm (PH7.0) 100ml.
After sterilization using a conventional method, Flavobacterium aquatile KK-111 (FERM P-10335) was inoculated.
A shaking culture was performed at 30°C, and the growth state, residual amount of triethanolamine and dissolved TOC were measured over time. The results are shown in Figure 1. As is clear from the figure, a decrease in triethanolamine and dissolved TOC was observed as the bacteria multiplied, and on the 9th day of culture, the decomposition rate of triethanolamine was over 99.9%, and the removal of dissolved TOC. The rate was also over 92%. Example 2 The same procedure as in Example 1 was carried out except that diethanolamine was used instead of triethanolamine. As a result, the decomposition rate of diethanolamine was 95% on the 6th day of culture. [Effects of the Invention] Since the microorganism of the present invention efficiently decomposes ethanolamines, it can be used to treat cutting oil waste fluid containing the ethanolamines.

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

第1図は、フラボバクテリウム・アクアタイル
KK−111の増殖状態とトリエタノールアミンお
よび溶存TOC濃度との関係を経時的に調べたグ
ラフである。
Figure 1 shows Flavobacterium aquatile
It is a graph showing the relationship between the proliferation state of KK-111 and the concentration of triethanolamine and dissolved TOC over time.

Claims (1)

【特許請求の範囲】[Claims] 1 エタノールアミン類を分解するフラボバクテ
リウム・アクアタイル。
1 Flavobacterium aquatile decomposes ethanolamines.
JP26064788A 1988-10-18 1988-10-18 Novel bacterium to decompose ethanolamines Granted JPH02109975A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP26064788A JPH02109975A (en) 1988-10-18 1988-10-18 Novel bacterium to decompose ethanolamines

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP26064788A JPH02109975A (en) 1988-10-18 1988-10-18 Novel bacterium to decompose ethanolamines

Publications (2)

Publication Number Publication Date
JPH02109975A JPH02109975A (en) 1990-04-23
JPH0441594B2 true JPH0441594B2 (en) 1992-07-08

Family

ID=17350821

Family Applications (1)

Application Number Title Priority Date Filing Date
JP26064788A Granted JPH02109975A (en) 1988-10-18 1988-10-18 Novel bacterium to decompose ethanolamines

Country Status (1)

Country Link
JP (1) JPH02109975A (en)

Families Citing this family (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS63239103A (en) * 1987-03-27 1988-10-05 Ulvac Corp Cubic boron nitride coated body and production thereof
US5686291A (en) * 1995-10-04 1997-11-11 Kabushiki Kaisha Neos Corynebacterium SP. N having decomposability for ethanolamines

Also Published As

Publication number Publication date
JPH02109975A (en) 1990-04-23

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