JPS62106898A - Microbiological treatment of waste liquid containing tetraalkylammonium salt or/and amines having methyl group - Google Patents

Microbiological treatment of waste liquid containing tetraalkylammonium salt or/and amines having methyl group

Info

Publication number
JPS62106898A
JPS62106898A JP24390085A JP24390085A JPS62106898A JP S62106898 A JPS62106898 A JP S62106898A JP 24390085 A JP24390085 A JP 24390085A JP 24390085 A JP24390085 A JP 24390085A JP S62106898 A JPS62106898 A JP S62106898A
Authority
JP
Japan
Prior art keywords
bacteria
amines
nocardia
activated sludge
waste liquid
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
JP24390085A
Other languages
Japanese (ja)
Other versions
JPH0615080B2 (en
Inventor
Kihachiro Misawa
三沢 輝八郎
Haruo Kurisu
治夫 栗栖
Tokuichi Oshimi
押見 篤一
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.)
Sumitomo Heavy Industries Envirotech Inc
Original Assignee
Sumitomo Heavy Industries Envirotech 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 Sumitomo Heavy Industries Envirotech Inc filed Critical Sumitomo Heavy Industries Envirotech Inc
Priority to JP24390085A priority Critical patent/JPH0615080B2/en
Publication of JPS62106898A publication Critical patent/JPS62106898A/en
Publication of JPH0615080B2 publication Critical patent/JPH0615080B2/en
Anticipated expiration legal-status Critical
Expired - Fee Related legal-status Critical Current

Links

Abstract

PURPOSE:To effectively perform the purification of waste water by decomposing amines, by adding Nocardia.SB-S-255 to activated sludge in which nitriding bacteria were propagated to perform the symbiotic propagation of both bacteria. CONSTITUTION:In decomposing tetraalkylammonium salt or trimethylamine, Nocardia.SB-S-255 (FERM P-8471) or a variant thereof is added to activated sludge in which nitriding bacteria were propagated to perform symbiotic propagation. In order to propagate nitriding bacteria present in activated sludge, ammonia or ammonium salt is added to the activated sludge. Further, a liquid medium suitable for the growth of Nocardia.SB-S-255 is put in a culture vessel and sterilized while the sterilized medium is inoculated with seed bacteria to perform aerobic culture. By this method, purification can be performed effectively and inexpensively.

Description

【発明の詳細な説明】 〔産業上の利用分野〕 本発明はテトラアルキルアンモニウム塩又は/及びメチ
ル基?有するアミン類含有廃液を処理方出に関″′する
[Detailed Description of the Invention] [Industrial Application Field] The present invention relates to tetraalkylammonium salts and/or methyl groups? This relates to the treatment of waste liquid containing amines.

〔従来の技術〕[Conventional technology]

近年、集積回路(IC)製造において現像液としてテト
ラメチルアンモニウムハイドロオキサイドナト ルアミンなどが使用されることが多い。そして便用後の
これらテトラアルキルアンモニウム塩やトリメチルアミ
ンなどを含有する現像廃l夜はn毒であり−また水質汚
濁の問題よりそのまま放流することができない。
In recent years, tetramethylammonium hydroxide natoluamine and the like are often used as developing solutions in the manufacture of integrated circuits (ICs). The developer waste containing these tetraalkylammonium salts, trimethylamine, etc. after urination is poisonous and cannot be discharged as it is due to water pollution problems.

現在,このようなテトラアルキルアンモニウム塩やトリ
メチルアミン等を含■する廃液よりこれら物質を除去し
て該廃液を浄化する手段として(ま。
Currently, it is being used as a means to purify the waste liquid by removing these substances from the waste liquid containing such tetraalkylammonium salts and trimethylamine.

逆浸透膜による処理(例えば特開昭60−//ざコ♂ユ
号公報)、あるいはこれにイオン交換樹脂による処理を
加えた処理が一般に行なわれているが、これら万広は処
理コストが高いという問題がある。
Treatment using a reverse osmosis membrane (for example, Japanese Unexamined Patent Application Publication No. 1983-1983) or treatment using an ion exchange resin is generally carried out, but these methods have high processing costs. There is a problem.

〔発明が解決しようとする問題点〕[Problem that the invention seeks to solve]

上記したように,テトラアルキルアンモニウム塩やトリ
メチルアミン等を含有する廃液よりこれら物質を除去し
て該廃液を浄化するために従来用いられている処理法で
は処理コストが高いといつ問題があり、上記廃液を安価
に処理できる万伍が望まれていたのであり−この間頂を
解決したのが本発明である。
As mentioned above, the treatment methods conventionally used to purify wastewater containing tetraalkylammonium salts, trimethylamine, etc. by removing these substances have the problem of high processing costs. There has been a desire for a solution that can be used at low cost, and the present invention solves this problem.

〔問題点を解決するための手段〕[Means for solving problems]

本発明者は一上記廃液を安価に処理する手段として微生
物を利用することに看目し、研究を進めた。
The present inventors focused on the use of microorganisms as a means of inexpensively treating the above-mentioned waste liquid, and proceeded with research.

しかしテトラアルキルアンモニウム塩やトリメチルアミ
ンなどは一般に微生物学的には非常に難分解性の化合物
であり1通常の所謂微生物学的な処理法では簡単に除去
できない。
However, tetraalkylammonium salts, trimethylamine, etc. are generally microbiologically extremely difficult to decompose compounds, and cannot be easily removed by conventional so-called microbiological treatment methods.

そこで本発明者は一テrラアルキルアンモニウム塩やト
リメチルアミンなどを分解する菌を自然界より見い出す
ことについて研究した結果、ついに手持ちの活性汚泥試
料中より、テトラアルキルアンモニウム塩やメチル基を
百するアミン類を単一の炭素源として利用できるノカル
ジア・エスピー3− a s s (Nocardia
 8p、 S−2!j )を分離した。そして更にこの
菌を一硝化菌を繁殖させた活性汚泥に添卯し共凄繁殖さ
せたものをテトラアルキルアンモニウム塩又は/及びメ
チル基を有するアミン類含■廃液の処理に用いろと、ノ
カルジア・エスピーS−236によりテトラアルキルア
ンモニウム塩又は/及びメチル基?■するアミン類が分
解除去され、その分解虫取物であるアンモニアも硝化菌
により硝化され、ノカルジア・エスピーS−,lj!お
よび他の菌により脱窒素されて上記廃水の浄化が効果的
に安価に行われること?見い出した。
Therefore, as a result of research to find bacteria that decompose tetraalkylammonium salts and trimethylamine in the natural world, the present inventor finally found tetraalkylammonium salts and amines with 100% methyl groups in activated sludge samples on hand. Nocardia sp.3-a ss (Nocardia sp.
8p, S-2! j) was separated. Furthermore, it was proposed that this bacterium should be added to activated sludge in which mononitrifying bacteria had been grown, and the resulting mixture should be used to treat wastewater containing tetraalkylammonium salts and/or amines having methyl groups. Tetraalkylammonium salt or/and methyl group by SP S-236? ■ Amines are decomposed and removed, and ammonia, which is the decomposed insect residue, is also nitrified by nitrifying bacteria, resulting in Nocardia sp. S-, lj! Is it possible to purify the wastewater effectively and inexpensively by denitrifying it with other bacteria? I found it.

本発明はこの細見に基づ(もので一本発明は硝トラアル
キルアンモニウム塩又は/及びメチル基を有するアミン
類含■廃液を処理して浄化すること?特徴とするテトラ
アルキルアンモニウム塩又は/及びメチル基を有するア
ミン類含■廃液を処理方伝である。
The present invention is based on this detailed observation (one aspect of the present invention is to treat and purify a waste liquid containing nitrate-alkylammonium salts and/or amines having methyl groups). This is a method for treating waste liquid containing amines with methyl groups.

本発明で使用するノカルジア・エスピーS −,2Jづ
の菌学的性質は下記の通りである。
The mycological properties of Nocardia sp. S-, 2J used in the present invention are as follows.

(a)形態 M胞の形及び大きさ二短桿菌、0.7!×ハ!μ細胞の
多形性:   ミセル→桿菌 運動性:       − 鞭毛:       − 胞子の有無:    − ダラム染色:    + 抗醗注:      + (1))各培地での生育状態 肉汁寒天平板培地: 培養28目で点状、直径/〜/、
!朋− 金縁、白濁色、光沢 なし、生育は中。
(a) Morphology: Shape and size of M vesicles, bilobal bacilli, 0.7! ×Ha! Pleomorphism of μ cells: Micelle → bacillus motility: - Flagella: - Presence of spores: - Durham staining: + Anti-injection: + (1)) Growth status in each medium Broth agar plate medium: At 28th culture point-like, diameter /~/,
! - Golden edge, cloudy color, no luster, medium growth.

肉汁寒天斜面培地: 症状、光沢なし、生育は中。Broth agar slant medium: Symptoms, no luster, medium growth.

肉汁液体培地:   沈渣、生育は小〜中。Meat juice liquid medium: Sediment, growth is small to medium.

肉汁ゼラチン培地: 30°C16日で液化せず、/な
日で液化 せず。
Meat juice gelatin medium: Not liquefied in 16 days at 30°C, not liquefied in / days.

リドマスミルク:   30′G−振盪培養で一7日目
にアルカリ性。
Lidomus milk: 30'G - alkaline on day 17 of shaking culture.

凝固、28目にアル カリ性、ペプトン1ヒ。Coagulation, alkaline at 28th Potash, peptone 1 h.

シュクロース・硝酸塩 寒天培地:      生育せず。Sucrose/nitrate Agar medium: No growth.

グリセリン・アスパラギン 寒天培地:       生育せず0 ペプトン・イースト鉄 寒天斜面培地:      症状、淡黄白濁−生育は大
Glycerin/asparagine agar medium: No growth (0) Peptone/yeast iron agar slant medium: Symptoms: pale yellow and cloudy - growth is large.

加糖ブイヨン寒天斜面 培地:        拡布状、表面しわ一黄土白濁、
生育は大。
Sweetened bouillon agar slant medium: spread-like, surface wrinkled, ocher cloudy,
Growth is large.

(c)生理学的性質 硝酸塩の還元:   + MRテスト:    + インドール虫取:  − デンプンの加水分解:    + ウレアーゼ:    + カタラーゼ:    + 酸素に対する態度: 好気性 生育のpH範囲:    s、5−to、。(c) Physiological properties Nitrate reduction: + MR test: + Indore insect retrieval: − Hydrolysis of starch: + Urease: + Catalase: + Attitude towards oxygen: aerobic Growth pH range: s, 5-to,.

生育の温度範囲:  /タ〜グ0 ’C糖の利用及びガ
スの発生: 糖の利用  ガスの発生 D−フラクトース    十     −D−グルコー
ス     +     −マルトース      −
− マンノース      −− ラムノース     −    − グリセロール    −− マンニトール    十    − D−ガラクトース    −     −イノシトール
    +    − ラクトース     −− シュクロース     −    − アドニトール    −    − L−アラビノース    −− リボース       十     −ソルビトール 
   十    − トレハロース     −− セルビオース    −− キシロース      −− デキストリン     −    − (d)その他の性質 り級アミン及びその池のアミン類の分解能:テトラメチ
ルアンモニウムハイドロオキサイド+テトラメチルアン
モニウムクロライド    +トリメチルアミン   
      +ジメチルアミン         + メチルアミン          + 上記の菌学的性質にしたがい、バージニーズ・マニュア
ル・オブ・ディタミネーティブ書バクテリオロジイ(B
ergey’s Manual of Determi
nativeBacteriolog)’ )第1版(
/9ンク〕ニより上記閑の同定を行なうと一該菌はノヵ
ルジア(Nocard ia )属に属する菌であるが
−特に糖の資化性が特異的で、種(3pcies )と
しては一致するものが見当らず、新種と判断された。
Temperature range for growth: /tag 0 'C Sugar utilization and gas generation: Sugar utilization Gas generation D-fructose 10 -D-glucose + -maltose -
− Mannose − − Rhamnose − − Glycerol − − Mannitol 10 − D-Galactose − − Inositol + − Lactose − − Sucrose − − Adonitol − − L-arabinose − − Ribose 10 − Sorbitol
10 − Trehalose − − Cellbiose − − Xylose − − Dextrin − − (d) Resolution of other basic amines and their amines: Tetramethylammonium hydroxide + Tetramethylammonium chloride + Trimethylamine
+ Dimethylamine + Methylamine + According to the above mycological properties,
ergey's Manual of Determi
native Bacteriology)' ) 1st edition (
/9] The identification of the above-mentioned bacteria from [2] shows that the bacteria belong to the genus Nocardia, but they are particularly unique in their ability to assimilate sugars, and the species (3pcies) are identical. was not found, and it was determined to be a new species.

なお、このノヵルジア・エスピーS−+26ICNoc
ardia 3p、 S −2r s )は、工業技術
院微生物工業技術研究所に微工研菌寄第?グ2/号(F
ERMP−♂4t7/ )として寄託されている0本発
明においては、ノカルジアーエスピー5−25夕げかり
でなく一該菌を常圧の変異手段により変異させた変異株
も使用することができろ。
In addition, this Nocardia sp. S-+26ICNoc
ardia 3p, S-2rs) was submitted to the Institute of Microbiological Technology, Agency of Industrial Science and Technology. 2/issue (F
ERMP-♂4t7/) In the present invention, not only Nocardia sp. .

ここで、このノカルジア・エスピーS−2オ!がテトラ
アルキルアンモニウム塩やメチル基ffaするアミン類
を分解除去する能力のあることを実験例を示して説明す
る。
Here, this Nocardia SP S-2O! The ability to decompose and remove tetraalkylammonium salts and amines containing methyl groups will be explained using experimental examples.

実験例 テトラメチルアンモニウムハイドロオキサ1イド100
0m9/Eを加糖ブイヨン(グルコース7%。
Experimental example Tetramethylammonium hydroxide 100
0m9/E sweetened bouillon (glucose 7%).

肉エキス/%−ペプトン1%%NaC1θ、j%)Km
加し、1)H7、θに調整した培地に、ノカルジア・エ
スピー3−2夕t(FERMP−♂タフl)を接種し、
30°Cでa日間振盪培養した培養物を遠心沈澱し、洗
菌したものを、菌体乾物量/θ0θm9/!となるよう
に、炭素源としてテトラメチルアンモニウムハイドロオ
キサ1ド(TMAHLテトラメチルアンモニウムクロラ
イド(TMAC)、テトラn−プロピルアンモニウムハ
イドロオキサイト0(TPAH)、テ)うn−プロピル
アンモニウムクロライl−’(TPAC)−テトラブチ
ルアンモニウムハ・fドロ、tキ?イ”゛(TBAH)
、テトラブチルアンモニウムクロライド(TBAC)−
)ジメチルアミンCTM、\)、ジメチルアミン(DM
A)、メチルアミン(MA)をそれぞれ含有するF記の
組成のtLコθ0 、nbに接種した。
Meat extract/%-Peptone 1%%NaC1θ,j%)Km
1) Inoculate Nocardia sp. 3-2t (FERMP-♂Tuffl) into a medium adjusted to H7,
The culture cultured with shaking at 30°C for a day was centrifuged and washed, and the dry weight of bacterial cells/θ0θm9/! Tetramethylammonium hydroxide 1 (TMAHL tetramethylammonium chloride (TMAC), tetra n-propylammonium hydroxide 0 (TPAH), te) n-propylammonium chloride l-' as a carbon source so that (TPAC) - Tetrabutylammonium ha-f-dro, t-ki? I”゛(TBAH)
, tetrabutylammonium chloride (TBAC)-
) dimethylamine CTM, \), dimethylamine (DM
A) and tL θ0 and nb having the composition shown in F containing methylamine (MA), respectively, were inoculated.

炭素源(m9/1.)1000 コーンスチーグリ力−(rn9/4)      30
0M//!りん酸バッファー(rn6 )      
  −〇総容量(ml )          200
pH7、oに調整 菌の接種後、30℃で2.2時間振儒培養し、2’、を
時間後、り?時間後、72時間後における液中の炭素源
である上記化合物のH(m9 / A ) ’2高速液
体クロマトグラフィー法(HPLCi)により測定した
。その結果?第1表に示す。
Carbon source (m9/1.) 1000 Cohn-Stiegley force (rn9/4) 30
0M//! Phosphate buffer (rn6)
-〇Total capacity (ml) 200
After inoculating the bacteria with a pH adjusted to 7.0°C, the shake culture was carried out at 30°C for 2.2 hours, and after 2 hours, the cells were cultured. H(m9/A)'2 of the above compound as a carbon source in the liquid after 72 hours was measured by high performance liquid chromatography (HPLCi). the result? Shown in Table 1.

第      1      表 上記第1表の結果から、ノカルジア拳エスピー5−uj
jがテトラアルギルアンモニウム塩又は/及びメチル基
を有するアミン類を分解除去するを硝化菌を繁殖させた
活性汚泥に添加し共棲繁殖させろ。
Table 1 From the results in Table 1 above, Nocardia Fist SP 5-uj
j is a tetraargylammonium salt or/and which decomposes and removes amines having a methyl group, and is added to the activated sludge in which nitrifying bacteria have been propagated, and allowed to coexist and proliferate.

硝化菌は一古(から土壌中の窒素1し合物のス化に関係
する農業上重要な土壌細菌として知られており、アンモ
ニアを亜硝酸に酸化してエネルギー’a’ ?Gるニト
ロソモナス(Nitrosomonas ) −亜硝酸
を硝酸に酸化してエネルギーを得ろニトロバクタ(N1
trobacter )などの菌がある。
Nitrifying bacteria have been known since ancient times as agriculturally important soil bacteria that are involved in the oxidation of nitrogen compounds in the soil. (Nitrosomonas) - Obtain energy by oxidizing nitrite to nitric acid. Nitrobacter (N1
trobacter).

活性汚泥は常伍にしたがって得ることができ。Activated sludge can be obtained as usual.

この活性汚泥に硝化菌を繁殖させるには、通常活性汚泥
にアンモニア又はアンモニウム塩を〕えてゆ(と〔この
場合1通気するのが好ましい)、汚泥中に存在する硝化
菌が繁殖してゆき、他の菌が淘汰されて/!日〜lケ月
位で硝化菌が繁殖した菌を繁殖させた活性汚泥に添加−
fるにあたっては一接菌を培養したもの又はこれより分
離した菌体を添加するのがよい0この培養は一般の細菌
のそれと同様に行なうことができる0即ち、接菌の生育
に好適な液体培地〔炭素源としてテトラアルキルアンモ
ニウム塩又は/及びメチル基を有するアミン類その他、
窒素源、必要に応じて無機塩、その他の栄蕃源など含再
)を培養器(例えば培養瓶。
In order to propagate nitrifying bacteria in this activated sludge, ammonia or ammonium salts are usually added to the activated sludge (and in this case, it is preferable to aerate the sludge), and the nitrifying bacteria present in the sludge propagate. Other bacteria have been culled/! Added to activated sludge in which nitrifying bacteria have grown for about 1 day to 1 month.
When culturing, it is best to add cultured bacteria or bacterial cells isolated from this culture. This culture can be carried out in the same way as for general bacteria. In other words, a liquid suitable for the growth of inoculated bacteria should be added. Medium [tetraalkylammonium salt or/and amines having a methyl group as a carbon source, etc.
Add a nitrogen source, inorganic salts if necessary, and other nutrient sources) to a culture vessel (for example, a culture bottle).

培養タンクなど]に入れ、殺菌し、菌の生育適温に調整
したものに別に調製した接菌の種菌を接種し一振急培養
1通気攪拌培養などの好気的培養を行ない国体の増殖を
はかる。この際、培地のpH及び温度は該jの最適な生
育条件に維持する。このようにして接菌の大量培養物′
ff?j%る。このようにして得たits物又はこれよ
り分離した菌体を。
Place in a culture tank, etc., sterilize and adjust the temperature to the appropriate temperature for bacterial growth, inoculate with a separately prepared inoculum, and perform aerobic culture such as one-shake rapid culture (1) aerated agitation culture to increase the growth of Kokutai. . At this time, the pH and temperature of the medium are maintained at the optimum growth conditions for j. In this way, a mass culture of inoculation
ff? j%ru. Its product thus obtained or bacterial cells isolated from it.

硝化菌を繁殖させた活性汚泥に添加する。その添垢量は
適当に選ぶことができるが一通常接菌の培量位で好結果
が得られろ。接菌を添加したら、炭素源としてのテトラ
アルキルアンモニウム塩又は/及びメチル基をHするア
ミン類、必要に応じて窒素源、無機塩などを添加して5
−io日位該接菌硝1じ菌を共妻繁殖させた活性汚泥で
処理すべきテトラアルキルアンモニウム塩又は/及びメ
チル基を有するアミン類含有廃i(例えばIC製造にお
けろ現像廃液など)!処理して浄化する手段。
Add to activated sludge that has grown nitrifying bacteria. The amount of addition can be selected appropriately, but good results will usually be obtained with the amount of culture used for inoculation. After adding the inoculation, add a tetraalkylammonium salt as a carbon source and/or amines that H hydrogen a methyl group, a nitrogen source, an inorganic salt, etc. as necessary.
-io date Waste containing tetraalkylammonium salts and/or amines having methyl groups to be treated with activated sludge in which the inoculated bacteria have been co-propagated (e.g. waste from development in IC manufacturing, etc.) ! Means of processing and purification.

操作は、常圧による廃液の微生物処理伝、即ちBOD除
去−硝化、脱窒素の好適条件C最適BOD負荷−最適窒
素負荷、最適酸素供給、最適無酸巽攪拌、最適pH及び
温度、不足栄養塩の補元等〕を維持しながら有機物及び
窒素を除去する方性におけると同様にして実施すること
ができろ。なお。
The operation consists of microbial treatment of waste liquid under normal pressure, i.e., BOD removal - nitrification, suitable conditions for denitrification. It can be carried out in the same manner as in the direction of removing organic matter and nitrogen while maintaining the complement of In addition.

上記廃液を処理する場合に、必要に応じて適量の燐酸塩
やコーンスチーブリカーなどのn機窒素源を廃液に添加
するのが好ましい。
When treating the above waste liquid, it is preferable to add an appropriate amount of nitrogen source such as phosphate or corn stew liquor to the waste liquid as necessary.

により従来を処理では除去が困難であった廃液中のテト
ラアルキルアンモニウム塩又は/及びメチル基を含有す
るアミン類が分解除去さおよび他の国により脱窒素され
るので、テトラアンモニウム塩又は/及びメチル基を有
するアミン類含■廃液の浄化を効果的にしかも安価に行
なうことができる。
The tetraalkylammonium salts and/or methyl group-containing amines in the waste liquid, which were difficult to remove by conventional treatments, are decomposed and removed and denitrified by other countries. Waste liquid containing amines having groups can be purified effectively and at low cost.

〔実施例〕〔Example〕

つぎに本発明の実施例を示す。 Next, examples of the present invention will be shown.

テトラメチルアンモニウムハイドロオキサイドCTMA
H)1000m9/Z’171Q糖7”イヨ7( !ル
コース/%,肉エキス1%,ペフトン/%. NaC1
θ.!%)に添加し.pH7.0に調整した培地0、コ
!に,ノカルジアeエスピーS−2!夕(FERM  
P−と4t7/)を接種し.30℃で3日間振盪培養し
た。この培養物を,常法で得た活性汚泥に塩1ヒアンモ
ニウムを添加し/ケ月位通気して硝化菌を繁殖させた活
性汚泥の入っている反応槽に添加し一適量のテトラメチ
ルアンモニウムハイドロオキサイト”( TMAH)を
卯え,ノカルジア・エスピー8−2srを/週間程度馴
養,育戊したO この反応槽の活性汚泥にテトラメチルアンモニウムハイ
ドロオキサイy(TMAH1含有廃水に適量の燐酸塩及
びコーンスチープリカーを補充した原水を通し,第2表
に示す負荷条件で滞留時間がグ3時間となるように処理
水の引抜きと原水の添1時間サイクル)シ,第2表に示
す良好な廃液処理の成果を得ることができた。なお、こ
こでは間欠曝気法による例を示したが、通常の循環型硝
化脱窒法による処理も可能である。第2表中+ TMA
Hは高速液体クロマトグラフィー伝(HPLC法)で測
定し,また工場排水試験方法JISーKotoコ−/9
♂/第グ乙頁によりTOC(総有機性炭素)を測定し.
同じ(第な7頁により!30Dを測定し。
Tetramethylammonium hydroxide CTMA
H) 1000m9/Z'171Q Sugar 7"Iyo7 (!Lucose/%, Meat Extract 1%, Peftone/%. NaC1
θ. ! %). Medium 0 adjusted to pH 7.0, Ko! , Nocardia eS-2! Evening (FERM)
P- and 4t7/) were inoculated. Shaking culture was carried out at 30°C for 3 days. This culture was added to a reaction tank containing activated sludge obtained by adding one hyammonium salt to activated sludge obtained by a conventional method and aerated for several months to propagate nitrifying bacteria. Nocardia sp. 8-2sr was acclimated and grown for about a week using Tetramethylammonium hydroxide (TMAH) in the activated sludge of this reaction tank. The raw water supplemented with corn steep liquor is passed through, under the load conditions shown in Table 2, the treated water is withdrawn and the raw water is added for a 1-hour cycle so that the residence time is 3 hours. We were able to obtain treatment results.Although an example using the intermittent aeration method is shown here, treatment using the normal circulating nitrification and denitrification method is also possible.+ TMA in Table 2
H is measured by high performance liquid chromatography (HPLC method), and factory wastewater test method JIS-Koto Co./9
Measure the TOC (total organic carbon) using the ♂/Part 2 page.
Same (according to page 7! Measured 30D.

同じ(第124を頁.第130頁−第132頁,第73
j頁により窒素化合物を測定し,その和を総窒素とした
Same (page 124, page 130 - page 132, page 73)
Nitrogen compounds were measured according to page J, and the sum was taken as the total nitrogen.

Claims (1)

【特許請求の範囲】[Claims] 硝化菌を繁殖させた活性汚泥にノカルジア・エスピーS
−255(Nocardia sp.S−255)又は
その変異株を添加し共棲繁殖させたもので、テトラアル
キルアンモニウム塩又は/及びメチル基を有するアミン
類含有廃液を処理して浄化することを特徴とするテトラ
アルキルアンモニウム塩又は/及びメチル基を有するア
ミン類含有廃液の微生物学的処理方法。
Nocardia sp. S in activated sludge with nitrifying bacteria
-255 (Nocardia sp. S-255) or a mutant strain thereof is added and co-propagated, and is characterized by treating and purifying waste liquid containing amines having tetraalkylammonium salts and/or methyl groups. A method for microbiological treatment of a waste liquid containing amines having a tetraalkylammonium salt and/or a methyl group.
JP24390085A 1985-11-01 1985-11-01 Microbiological treatment method for waste liquid containing tetraalkylammonium salt and / or amines having methyl group Expired - Fee Related JPH0615080B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP24390085A JPH0615080B2 (en) 1985-11-01 1985-11-01 Microbiological treatment method for waste liquid containing tetraalkylammonium salt and / or amines having methyl group

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP24390085A JPH0615080B2 (en) 1985-11-01 1985-11-01 Microbiological treatment method for waste liquid containing tetraalkylammonium salt and / or amines having methyl group

Publications (2)

Publication Number Publication Date
JPS62106898A true JPS62106898A (en) 1987-05-18
JPH0615080B2 JPH0615080B2 (en) 1994-03-02

Family

ID=17110666

Family Applications (1)

Application Number Title Priority Date Filing Date
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Country Status (1)

Country Link
JP (1) JPH0615080B2 (en)

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2009119521A1 (en) * 2008-03-26 2009-10-01 株式会社神鋼環境ソリューション Method for processing waste water
JP2009226325A (en) * 2008-03-24 2009-10-08 Japan Organo Co Ltd Water treatment method and water treatment apparatus

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2009226325A (en) * 2008-03-24 2009-10-08 Japan Organo Co Ltd Water treatment method and water treatment apparatus
WO2009119521A1 (en) * 2008-03-26 2009-10-01 株式会社神鋼環境ソリューション Method for processing waste water
JP2009255067A (en) * 2008-03-26 2009-11-05 Kobelco Eco-Solutions Co Ltd Method for processing waste water

Also Published As

Publication number Publication date
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