JPH0686998A - Method for removing phenols and anilines in water - Google Patents

Method for removing phenols and anilines in water

Info

Publication number
JPH0686998A
JPH0686998A JP4264284A JP26428492A JPH0686998A JP H0686998 A JPH0686998 A JP H0686998A JP 4264284 A JP4264284 A JP 4264284A JP 26428492 A JP26428492 A JP 26428492A JP H0686998 A JPH0686998 A JP H0686998A
Authority
JP
Japan
Prior art keywords
anilines
phenol
phenols
enzyme
oxidation
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
JP4264284A
Other languages
Japanese (ja)
Other versions
JPH06102200B2 (en
Inventor
Shinji Wada
慎二 和田
Hiroyasu Ichikawa
廣保 市川
Kenji Tatsumi
憲司 辰巳
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.)
National Institute of Advanced Industrial Science and Technology AIST
Original Assignee
Agency of Industrial Science and Technology
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 Agency of Industrial Science and Technology filed Critical Agency of Industrial Science and Technology
Priority to JP4264284A priority Critical patent/JPH06102200B2/en
Publication of JPH0686998A publication Critical patent/JPH0686998A/en
Publication of JPH06102200B2 publication Critical patent/JPH06102200B2/en
Anticipated expiration legal-status Critical
Expired - Lifetime legal-status Critical Current

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  • Separation Of Suspended Particles By Flocculating Agents (AREA)
  • Removal Of Specific Substances (AREA)
  • Treatment Of Water By Oxidation Or Reduction (AREA)

Abstract

PURPOSE:To make it possible to remove phenols and anilines by adding a cationic flocculant having an amine group and a phenol oxidation enzyme together, although the activity of enzyme is lost due to the bonding of an oxidation product with enzyme and the oxidation product remains unremoved, in a treatment of phenols and anilines in water using phenol oxidation enzyme. CONSTITUTION:Water containing phenols and/or anilines is treated by adding cationic flocculant having an amino group and a phenol oxidation enzyme together. Consequently, an oxidation product generated by catalytic oxidation of phenol oxidation enzyme is allowed to react with the cationic flocculant having an amino group very easily. Therefore, it is possible to oxidize phenols and anilines with the concurrent prevention of enzyme from losing its activity by bonding of the oxidation product with the cationic flocculant having an amino group, and at the same time, remove the oxidation product easily by flocculation.

Description

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

【0001】[0001]

【産業上の利用分野】本発明は、水中のフェノ−ル類及
びアニリン類の除去方法で、フェノ−ル酸化酵素及びア
ミノ基を有する陽イオン性凝集剤を併用して、該凝集剤
により酵素の失活を防ぎながら、フェノ−ル酸化酵素の
触媒作用による酸化を行わせるとともに、その酸化生成
物を該凝集剤により凝集して除去することにより、上水
処理、工業用水処理、排水処理、廃棄物浸出水処理等に
利用される。
FIELD OF THE INVENTION The present invention relates to a method for removing phenols and anilines in water, wherein a phenol oxidase and a cationic flocculant having an amino group are used in combination and the enzyme is coagulated by the flocculating agent. While preventing the inactivation of the, while carrying out the oxidation by the catalytic action of phenol oxidase, by aggregating and removing the oxidation product by the aggregating agent, clean water treatment, industrial water treatment, wastewater treatment, Used for waste leachate treatment.

【0002】[0002]

【従来の技術】合成有機化学工場、コ−クス工場等から
の排水には種々のフェノ−ル類及びアニリン類が含まれ
ており、これらの排水の処理には、従来、吸着法、抽出
法、イオン交換法、酸化法、生物処理法等が検討されて
きているが、実用的には生物処理法(活性汚泥法)のみ
が行われている。しかし、この生物処理法においても、
これらの化合物は生物分解性が低く、また、毒性を有す
るので、生物活性が阻害され、処理が十分に行われない
ため、生物分解されずに環境へ放出されているものも多
い。したがって、これらの化合物の安価で簡単な処理法
の開発が期待されている。
2. Description of the Related Art Wastewater from synthetic organic chemical plants, coke plants, etc. contains various phenols and anilines. The treatment of these wastewaters has hitherto been carried out by an adsorption method and an extraction method. , Ion exchange method, oxidation method, biological treatment method, etc. have been studied, but only biological treatment method (activated sludge method) is practically used. However, even in this biological treatment method,
Since these compounds have low biodegradability and are toxic, their biological activity is inhibited and treatment is not carried out sufficiently, and therefore many of them are released into the environment without being biodegraded. Therefore, development of an inexpensive and simple treatment method for these compounds is expected.

【0003】フェノ−ル類及びアニリン類の安価で簡単
な処理法として考えられるのは酵素の触媒作用を利用す
る処理法である。これまでにもフェノ−ル酸化酵素を利
用する試みはいくつかなされてきたが、これには二つの
重要な欠点がある。それはフェノ−ル酸化酵素が、フェ
ノ−ル類やアニリン類の酸化生成物と結合して失活して
しまうことと、フェノ−ル類やアニリン類の酸化生成物
は水中に溶存したままで、除去されないことである。
An inexpensive and simple treatment method for phenols and anilines is a treatment method utilizing the catalytic action of an enzyme. There have been some attempts to utilize phenol oxidase, but this has two important drawbacks. That is, the phenol oxidase is inactivated by binding with the oxidation products of phenols and anilines, and the oxidation products of phenols and anilines remain dissolved in water. It is not removed.

【0004】[0004]

【発明が解決しようとする課題】これまでのフェノ−ル
酸化酵素を利用した処理には、上記の重要な欠点があ
る。本発明が解決しようとする課題は、フェノ−ル類及
びアニリン類の酸化生成物の完全な除去とフェノ−ル酸
化酵素の失活の防止である。
The conventional treatments using phenol oxidase have the above-mentioned important drawbacks. The problem to be solved by the present invention is to completely remove the oxidation products of phenols and anilines and prevent the inactivation of phenol oxidase.

【0005】[0005]

【課題を解決するための手段】本発明者は、フェノ−ル
類やアニリン類の酸化生成物が、アミノ基を有する陽イ
オン性凝集剤と容易に結合することを見いだした。した
がって、フェノ−ル酸化酵素及びアミノ基を有する陽イ
オン性凝集剤を併用すれば、酵素の失活を防止するとと
もに、酸化生成物を容易に凝集して除去することができ
ると考えられる。本発明は、フェノ−ル酸化酵素及びア
ミノ基を有する陽イオン性凝集剤を併用して、該凝集剤
により酵素の失活を防ぎながら、上記フェノ−ル類及び
(または)アニリン類をフェノ−ル酸化酵素で酸化する
とともに、酸化生成物を該凝集剤により凝集・除去する
方法である。
The present inventor has found that the oxidation products of phenols and anilines can easily bind to a cationic flocculant having an amino group. Therefore, it is considered that when phenol oxidase and a cationic flocculant having an amino group are used in combination, the inactivation of the enzyme can be prevented and the oxidation product can be easily flocculated and removed. In the present invention, a phenol oxidase and a cationic flocculant having an amino group are used in combination, and the phenols and / or anilines are treated with phenol while preventing the enzyme from being deactivated by the flocculant. It is a method of oxidizing with a oxidase and aggregating and removing the oxidation product with the aggregating agent.

【0006】本発明で、フェノ−ル類とは、フェノ−ル
及びクロロフェノ−ル、メトキシフェノ−ル、クレゾ−
ル、ヒドロキシフェノ−ル等、フェノ−ル置換体を、ア
ニリン類とは、アニリン及びp−クロロアニリン、3,
4−ジクロロアニリン等、アニリン置換体をいう。
In the present invention, the phenols are phenol, chlorophenol, methoxyphenol and cresol.
And phenol substituted products such as hydroxyphenol and anilines, aniline and p-chloroaniline, 3,
An aniline-substituted product such as 4-dichloroaniline.

【0007】本発明で、フェノ−ル酸化酵素とは、チロ
シナ−ゼ、ラッカ−ゼ、ペルオキシダ−ゼ、ポリフェノ
−ルオキシダ−ゼ等をいう。チロシナ−ゼ及びラッカ−
ゼ等は酸素存在下(空気中でよい)で、ペルオキシダ−
ゼ等は過酸化水素存在下でフェノ−ル類やアニリン類の
酸化を触媒する。チロシナ−ゼは市販の精製された酵素
でもよく、また、マッシュル−ム等この酵素を含有する
動物、植物、微生物由来の試料でもよい。ラッカ−ゼは
市販の酵素でもよく、この酵素を含有する動物、植物、
微生物由来の試料でもよい。ペルオキシダ−ゼは市販の
酵素でもよく、西洋わさび等この酵素を含有する動物、
植物、微生物由来の試料でもよい。
In the present invention, the phenol oxidase means tyrosinase, laccase, peroxidase, polyphenol oxidase and the like. Tyrosinase and lacquer
In the presence of oxygen (good in air), peroxida
Ze and the like catalyze the oxidation of phenols and anilines in the presence of hydrogen peroxide. Tyrosinase may be a commercially available purified enzyme, or may be a sample derived from animals, plants, or microorganisms containing this enzyme such as mashroom. The laccase may be a commercially available enzyme, and animals, plants,
A sample derived from a microorganism may be used. Peroxidase may be a commercially available enzyme, such as horseradish, animals containing this enzyme,
Samples derived from plants or microorganisms may be used.

【0008】本発明で、アミノ基とは置換アミノ基を含
む。アミノ基を有する陽イオン性凝集剤としては、アミ
ン−エピクロロヒドリン重縮合物、ポリアルキレンポリ
アミン、ポリアクリル酸アミノエチルエステル、ポリメ
タクリル酸アミノエチルエステル、ポリアクリルアミド
のカチオン変成物、キトサン等が含まれる。
In the present invention, the amino group includes a substituted amino group. As the cationic flocculant having an amino group, amine-epichlorohydrin polycondensate, polyalkylene polyamine, polyacrylic acid aminoethyl ester, polymethacrylic acid aminoethyl ester, polyacrylamide cation modified product, chitosan, etc. included.

【0009】酵素触媒酸化反応の条件は、反応温度は1
0〜50℃で10〜30℃が最適であり、pHは4〜9
でよく、pH6〜8が最適である。凝集剤の添加量は、
フェノ−ル類及びアニリン類の濃度と関連し、あらかじ
め予備試験をして決めるが、0.1〜100mg/lが
よい。フェノ−ル酸化酵素は、緩衝液に1mg/ml以
上の濃度に溶解して添加するのがよい。また、フェノ−
ル酸化酵素は、担体に固定化して用いてもよい。
The condition of the enzyme-catalyzed oxidation reaction is that the reaction temperature is 1
The optimum temperature is 0 to 50 ° C and 10 to 30 ° C.
And pH 6-8 is optimal. The amount of coagulant added is
The concentration of phenols and anilines is related to the concentration of phenols and anilines, and is determined by a preliminary test in advance. The phenol oxidase is preferably added after being dissolved in a buffer solution at a concentration of 1 mg / ml or more. In addition,
The luoxidase may be used after being immobilized on a carrier.

【0010】フェノ−ル酸化酵素で酸化しにくいフェノ
−ル類及びアニリン類の場合には、反応を促進するため
に助剤を添加して、その酸化物とフェノ−ル類及びアニ
リン類との重合を行わせてもよい。添加する助剤は酵素
により異なる。例えば、チロシナ−ゼ(マッシュル−ム
起源)及びペルオキシダ−ゼ(西洋わさび起源)の場合
にはフェノ−ル等を添加し、ラッカ−ゼ(いもち病菌起
源)の場合はo−メトキシフェノ−ル等を添加する。
In the case of phenols and anilines which are difficult to be oxidized by phenol oxidase, an auxiliary agent is added to accelerate the reaction so that the oxides can be separated from the phenols and anilines. Polymerization may be performed. The auxiliary agent added depends on the enzyme. For example, in the case of tyrosinase (origin from mashleum) and peroxidase (origin from horseradish), phenol and the like are added, and in the case of laccase (origin from blast fungus), o-methoxyphenol and the like. Is added.

【0011】チロシナ−ゼ及びラッカ−ゼの場合は、酸
化反応は酸素を必要とするので、空気中でかくはんする
か、酸素または空気を通気するのがよい。ペルオキシダ
−ゼの場合は、過酸化水素の添加が必要である。また、
これらの酸素及び過酸化水素は化学反応等により生成さ
せてもよい。
In the case of tyrosinase and laccase, the oxidation reaction requires oxygen, so it is preferable to stir in air or aerate oxygen or air. In the case of peroxidase, the addition of hydrogen peroxide is necessary. Also,
These oxygen and hydrogen peroxide may be generated by a chemical reaction or the like.

【0012】凝集剤は、はじめから添加しておいてもよ
く、フェノ−ル酸化酵素による酸化の途中または後で添
加してもよい。チロシナ−ゼ及びラッカ−ゼの場合に
は、失活が遅いので、凝集剤の添加は酸化の途中または
後でもよい。ペルオキシダ−ゼの場合には、該酵素はと
くにフェノ−ル類の酸化物とただちに結合して失活する
ので、それを防止するためはじめからアミノ基を有する
陽イオン性凝集剤を添加するほうがよい。
The coagulant may be added from the beginning or may be added during or after the oxidation by the phenol oxidase. In the case of tyrosinase and laccase, the inactivation is slow, and thus the coagulant may be added during or after the oxidation. In the case of peroxidase, the enzyme specifically binds to the oxides of phenols immediately and inactivates, so it is better to add a cationic coagulant having an amino group from the beginning to prevent it. .

【0013】凝集した酸化生成物は、沈殿させて除去し
てもよく、濾過、遠心分離、浮上分離等の方法で除去し
てもよい。
The agglomerated oxidation product may be removed by precipitation, or may be removed by a method such as filtration, centrifugation or flotation.

【0014】[0014]

【発明の作用】フェノ−ル酸化酵素の触媒作用によりフ
ェノ−ル類及びアニリン類は酸化され酸化生成物が生成
するが、フェノ−ル酸化酵素はこれらの酸化生成物と結
合して失活し、また、それらの酸化生成物は水中に溶存
したままであり、除去されない。本発明は、フェノ−ル
類及びアニリン類の酸化生成物がアミノ基を有する陽イ
オン性凝集剤と容易に結合する性質があることを利用し
て次の作用を行わせる。フェノ−ル酸化酵素及びアミノ
基を有する陽イオン性凝集剤を併用することにより、酸
化生成物は該凝集剤と容易に結合するため酵素が失活し
ない。また、酸化生成物は該凝集剤と容易に結合して凝
集し、完全に除去されるものである。
The phenol oxidase catalyzes the oxidation of phenols and anilines to produce oxidation products. The phenol oxidases are inactivated by binding with these oxidation products. Also, their oxidation products remain dissolved in water and are not removed. The present invention takes advantage of the fact that the oxidation products of phenols and anilines have a property of easily binding to a cationic flocculant having an amino group, and the following actions are performed. When the phenol oxidase and the cationic flocculant having an amino group are used in combination, the oxidation product is easily bound to the flocculant, so that the enzyme is not inactivated. Further, the oxidation product is one that is easily combined with the aggregating agent and aggregates to be completely removed.

【0015】[0015]

【実施例1】フェノ−ル0.5mM、チロシナ−ゼ(S
IGMA社製、マッシュル−ム起源)20U(酵素単
位)/ml及びリン酸緩衝液5mM(pH 7.0)を
含有する反応液を空気中で室温でかくはんした。30分
後のフェノ−ル類除去率は100%で、褐色の溶液とな
ったが、沈殿しない。この溶液にヘキサメチレンジアミ
ン−エピクロロヒドリン重縮合物またはポリエチレンイ
ミン市販品20mg/lを添加しそれぞれかくはんした
ところ、いずれも凝集し、上澄液は無色透明の液となっ
た。
Example 1 Phenol 0.5 mM, tyrosinase (S
A reaction solution containing 20 U (enzyme unit) / ml (manufactured by IGMA, origin of mushroom) and 5 mM phosphate buffer (pH 7.0) was stirred in the air at room temperature. After 30 minutes, the removal rate of phenols was 100%, and a brown solution was obtained, but no precipitation occurred. When 20 mg / l of a hexamethylenediamine-epichlorohydrin polycondensate or a polyethyleneimine commercial product was added to this solution and stirred, each coagulated, and the supernatant liquid became a colorless and transparent liquid.

【0016】他方、非イオン性凝集剤ポリアクリルアミ
ド市販品を、チロシナ−ゼで酸化した上記反応溶液に2
0、50及び100mg/l添加したが、いずれも全く
凝集効果は見られなかった。
On the other hand, a commercially available nonionic flocculant polyacrylamide was added to the above reaction solution which had been oxidized with tyrosinase.
0, 50 and 100 mg / l were added, but no aggregation effect was observed.

【0017】フェノ−ル0.5mM、チロシナ−ゼ20
U/ml、リン酸緩衝液5mM(pH 7.0)及びヘ
キサメチレンジアミン−エピクロロヒドリン重縮合物2
0mg/lを含有する反応液を室温でかくはんした。2
0分後のフェノ−ル除去率は100%で、褐色のフロッ
クを生成し沈殿し、上澄液は無色透明の液となった。
Phenol 0.5 mM, tyrosinase 20
U / ml, phosphate buffer 5 mM (pH 7.0) and hexamethylenediamine-epichlorohydrin polycondensate 2
The reaction containing 0 mg / l was stirred at room temperature. Two
The phenol removal rate after 0 minutes was 100%, brown flocs were formed and precipitated, and the supernatant became a colorless and transparent liquid.

【0018】また、フェノ−ル0.5mM水溶液に凝集
剤ヘキサメチレンジアミン−エピクロロヒドリン重縮合
物のみを、10、20、40、80、200及び400
mg/l添加しても、いずれも全く凝集効果は見られな
かった。すなわち、フェノ−ル自体は凝集剤で凝集でき
ないが、チロシナ−ゼでフェノ−ルを酸化することによ
って凝集可能な形態に変わったのである。
Further, only the coagulant hexamethylenediamine-epichlorohydrin polycondensate was added to a 0.5 mM aqueous solution of phenol for 10, 20, 40, 80, 200 and 400.
Even if mg / l was added, no aggregation effect was observed. That is, the phenol itself could not be aggregated by the aggregating agent, but it was transformed into a form capable of aggregating by oxidizing the phenol with tyrosinase.

【0019】なお、ヘキサメチレンジアミン−エピクロ
ロヒドリン重縮合物の合成は次の方法によった。ヘキサ
メチレンジアミン20gをとり、水40gを加え、等モ
ル量のエピクロロヒドリン15.9gを徐々に添加し、
45℃で50分間かくはんした後、水で2倍に希釈し、
さらに45℃で20分間かくはんした。得られた重縮合
物は、塩酸でpHを4に調節し、濃度を5%に希釈し
た。この重縮合物の濃度1%溶液の20℃における水に
対する相対粘度は4.8である。
The hexamethylenediamine-epichlorohydrin polycondensate was synthesized by the following method. Take 20 g of hexamethylenediamine, add 40 g of water, and slowly add 15.9 g of an equimolar amount of epichlorohydrin,
After stirring at 45 ° C for 50 minutes, dilute 2 times with water,
The mixture was stirred at 45 ° C for 20 minutes. The pH of the obtained polycondensate was adjusted to 4 with hydrochloric acid, and the concentration was diluted to 5%. The relative viscosity of the 1% concentration solution of this polycondensate to water at 20 ° C. is 4.8.

【0020】[0020]

【実施例2】p−クロロフェノ−ル、p−メトキシフェ
ノ−ル、m−クレゾ−ル、p−クレゾ−ルまたはカテコ
−ル0.5mM、チロシナ−ゼ20U/ml及びリン酸
緩衝液5mM(pH 7.0)を含有する反応液5種を
それぞれ空気中で室温でかくはんした。30分後のフェ
ノ−ル類除去率はいずれも100%で、褐色の溶液とな
ったが、沈殿しない。この溶液にヘキサメチレンジアミ
ン−エピクロロヒドリン重縮合物またはポリエチエンイ
ミン市販品20mg/lを添加しそれぞれかくはんした
ところ、いずれも凝集し、上澄液は無色透明の液となっ
た。
Example 2 p-chlorophenol, p-methoxyphenol, m-cresol, p-cresol or catechol 0.5 mM, tyrosinase 20 U / ml and phosphate buffer 5 mM ( Each of the 5 reaction solutions containing pH 7.0) was stirred in air at room temperature. The removal rate of phenols after 30 minutes was 100% in all, and a brown solution was obtained, but no precipitation occurred. When 20 mg / l of a hexamethylenediamine-epichlorohydrin polycondensate or a polyethyleneimine commercial product was added to this solution and stirred, each coagulated, and the supernatant liquid became a colorless and transparent liquid.

【0021】[0021]

【実施例3】o−クロロフェノ−ル、m−クロロフェノ
−ル、o−メトキシフェノ−ル、m−メトキシフェノ−
ル、o−クレゾ−ル、レゾルシンまたはヒドロキノン
0.5mM、チロシナ−ゼ100U/ml、フェノ−ル
1.5mM及びリン酸緩衝液5mM(pH 7.0)を
含有する反応液7種をそれぞれ空気中で室温でかくはん
した。1時間後のフェノ−ル類の除去率はいずれも10
0%で、褐色の溶液となったが、沈殿しない。これらの
溶液にヘキサメチレンジアミン−エピクロロヒドリン重
縮合物40〜60mg/lを添加しそれぞれかくはんし
たところ、いずれも凝集し、上澄液は無色透明の液とな
った。このように、単独では酸化しにくいフェノ−ル類
についても、フェノ−ルを助剤として添加することによ
りフェノ−ル酸化物と重合させ、それらをアミノ基を有
する陽イオン性凝集剤によって凝集・除去することがで
きる。
Example 3 o-chlorophenol, m-chlorophenol, o-methoxyphenol, m-methoxyphenol
Of the reaction liquid containing 0.5 mM of ole, o-cresol, resorcin or hydroquinone, 100 U / ml of tyrosinase, 1.5 mM of phenol, and 5 mM of phosphate buffer (pH 7.0) in air. Stirred at room temperature in. The removal rate of phenols after 1 hour is 10
0% gave a brown solution but no precipitation. When 40 to 60 mg / l of hexamethylenediamine-epichlorohydrin polycondensate was added to each of these solutions and stirred, each coagulated and the supernatant became a colorless and transparent liquid. Thus, even for phenols which are difficult to oxidize by themselves, they are polymerized with the phenol oxide by adding phenol as an auxiliary agent, and agglomerate them with a cationic flocculant having an amino group. Can be removed.

【0022】[0022]

【実施例4】アニリン、p−クロロアニリン及び3,4
−ジクロロアニリンのアニリン類もまた単独ではチロシ
ナ−ゼで酸化することができないが、フェノ−ルを助剤
として加えることによりフェノ−ル酸化物と重合させ、
これらをアミノ基を有する陽イオン性凝集剤によって凝
集除去することができる。これらのアニリン類0.5m
M、チロシナ−ゼ50U/ml、フェノ−ル0.5m
M、リン酸緩衝液5mM(pH 7.0)を含有する反
応液3種をそれぞれ空気中で室温でかくはんした。1時
間後のアニリン類の除去率はいずれも100%で、褐色
の溶液となったが、沈殿しない。これらの溶液にヘキサ
メチレンジアミン−エピクロロヒドリン重縮合物20〜
30mg/lを添加しかくはんしたところ、いずれも凝
集し、上澄液は無色透明の液となった。
Example 4 Aniline, p-chloroaniline and 3,4
-The anilines of dichloroaniline cannot also be oxidized by tyrosinase by themselves, but by adding phenol as an auxiliary agent to polymerize with phenol oxide,
These can be coagulated and removed by a cationic coagulant having an amino group. 0.5m of these anilines
M, tyrosinase 50U / ml, phenol 0.5m
The three reaction solutions containing M and 5 mM phosphate buffer (pH 7.0) were each stirred in air at room temperature. The removal rate of anilines after 1 hour was 100% in all, and a brown solution was obtained, but no precipitation occurred. Hexamethylenediamine-epichlorohydrin polycondensate 20-
When 30 mg / l was added and the mixture was stirred, all were aggregated, and the supernatant became a colorless and transparent liquid.

【0023】[0023]

【実施例5】o−メトキシフェノ−ルまたはカテコ−ル
0.5mM、ラッカ−ゼ(SIGMA社製、いもち病菌
起源)100U/ml及びリン酸緩衝液5mM(pH
6.5)を含有する反応液2種をそれぞれ空気中で室温
でかくはんした。1時間後のフェノ−ル類除去率はいず
れも100%で、褐色の溶液となったが沈殿しない。こ
の溶液にヘキサメチレンジアミン−エピクロロヒドリン
重縮合物20mg/lを添加しかくはんしたところ、い
ずれも凝集し、上澄液は無色透明の液となった。
Example 5 0.5 mM of o-methoxyphenol or catechol, 100 U / ml of laccase (manufactured by SIGMA, origin of blast fungus) and 5 mM of phosphate buffer (pH)
The two reaction solutions containing 6.5) were each stirred in air at room temperature. The removal rate of phenols after 1 hour was 100% in all, and a brown solution was obtained, but no precipitation occurred. When 20 mg / l of hexamethylenediamine-epichlorohydrin polycondensate was added to this solution and stirred, both were aggregated and the supernatant became a colorless and transparent liquid.

【0024】[0024]

【実施例6】アニリン、p−クロロアニリン及び3,4
−ジクロロアニリンのアニリン類は単独では上記ラッカ
−ゼで触媒酸化することができないが、o−メトキシフ
ェノ−ルを助剤として加えることによりこの酸化物と重
合させ、アミノ基を有する陽イオン性凝集剤によって凝
集除去することができる。これらのアニリン類0.5m
M、ラッカ−ゼ100U/ml、o−メトキシフェノ−
ル1.0mM及びリン酸緩衝液5mM(pH 6.5)
を含有する反応液3種をそれぞれ空気中で室温でかくは
んした。1時間後のアニリン類及びフェノ−ル除去率は
いずれも100%で、褐色の溶液となったが、沈殿しな
い。これらの溶液にヘキサメチレンジアミン−エピクロ
ロヒドリン重縮合物20〜30mg/lを添加しかくは
んしたところ、いずれも凝集し、上澄液は無色透明の液
となった。
Example 6 Aniline, p-chloroaniline and 3,4
-The anilines of dichloroaniline cannot be catalytically oxidized by the above-mentioned laccase by themselves, but they are polymerized with this oxide by adding o-methoxyphenol as an auxiliary agent, and cationic aggregation having an amino group is carried out. It can be coagulated and removed by the agent. 0.5m of these anilines
M, laccase 100 U / ml, o-methoxypheno-
1.0 mM and phosphate buffer 5 mM (pH 6.5)
Each of the three reaction solutions containing was stirred at room temperature in air. The removal rate of aniline and phenol after 1 hour was 100%, and a brown solution was obtained, but no precipitation occurred. When 20 to 30 mg / l of hexamethylenediamine-epichlorohydrin polycondensate was added and stirred to these solutions, all were aggregated, and the supernatant liquid became a colorless and transparent liquid.

【0025】[0025]

【実施例7】フェノ−ル0.5mM、過酸化水素0.5
mM、ペルオキシダ−ゼ(和光純薬製、西洋わさび起
源)1U/ml及びリン酸緩衝液5mM(pH 7.
0)を含有する反応液を室温でかくはんした。10分後
のフェノ−ル除去率は100%で、褐色の溶液となった
が、沈殿しない。この溶液にヘキサメチレンジアミン−
エピクロロヒドリン重縮合物20mg/lを添加しかく
はんしたところ、凝集し、上澄液は無色透明の液となっ
た。
[Example 7] Phenol 0.5 mM, hydrogen peroxide 0.5
mM, peroxidase (manufactured by Wako Pure Chemical Industries, origin of horseradish) 1 U / ml and phosphate buffer 5 mM (pH 7.
The reaction solution containing 0) was stirred at room temperature. The phenol removal rate after 10 minutes was 100%, and a brown solution was obtained, but no precipitation occurred. Hexamethylenediamine-
When 20 mg / l of epichlorohydrin polycondensate was added and stirred, the mixture agglomerated and the supernatant became a colorless and transparent liquid.

【0026】[0026]

【実施例8】フェノ−ル5mM、過酸化水素5mM、ペ
ルオキシダ−ゼ(和光純薬製、西洋わさび起源)2U/
ml、リン酸緩衝液5mM(pH 7.0)及びヘキサ
メチレンジアミン−エピクロロヒドリン重縮合物100
mg/lを含有する反応液を室温でかくはんした。1時
間後のフェノ−ル除去率は100%で、褐色のフロック
を生成し沈殿し、上澄液は無色透明の液となった。凝集
剤を添加しない場合には、1時間後のフェノ−ル除去率
は29.4%で、褐色の溶液であり、その後、時間が経
過しても同じ除去率のままであった。すなわち、凝集剤
を添加しないと急速に酵素が失活してしまうことを示し
ている。
Example 8 Phenol 5 mM, hydrogen peroxide 5 mM, peroxidase (Wako Pure Chemical Industries, Ltd., horseradish origin) 2 U /
ml, phosphate buffer 5 mM (pH 7.0) and hexamethylenediamine-epichlorohydrin polycondensate 100
The reaction containing mg / l was stirred at room temperature. The phenol removal rate after 1 hour was 100%, brown flocs were produced and precipitated, and the supernatant became a colorless and transparent liquid. When the flocculant was not added, the phenol removal rate after 1 hour was 29.4%, which was a brown solution, and remained the same removal rate over time. That is, it indicates that the enzyme is rapidly deactivated unless a coagulant is added.

【0027】[0027]

【実施例9】アニリン0.5mM、過酸化水素0.5m
M、ペルオキシダ−ゼ2U/ml及びリン酸緩衝液5m
M(pH 7.0)を含有する反応液を室温でかくはん
した。1時間後のアニリン除去率は100%で、褐色の
溶液となったが、沈殿しない。この溶液にヘキサメチレ
ンジアミン−エピクロロヒドリン重縮合物1.5mg/
lを添加しかくはんしたところ、凝集し、上澄液は無色
透明の液となった。
[Example 9] Aniline 0.5 mM, hydrogen peroxide 0.5 m
M, peroxidase 2U / ml and phosphate buffer 5m
The reaction containing M (pH 7.0) was stirred at room temperature. The aniline removal rate after 1 hour was 100%, and a brown solution was obtained, but no precipitation occurred. 1.5 mg of hexamethylenediamine-epichlorohydrin polycondensate in this solution
When 1 was added and stirred, the mixture agglomerated and the supernatant became a colorless and transparent liquid.

【0028】[0028]

【実施例10】3,4−ジクロロアニリンは単独ではペ
ルオキシダ−ゼで触媒酸化することができないが、フェ
ノ−ルを助剤として加えることによりフェノ−ル酸化物
と重合させ、これをアミノ基を有する陽イオン性凝集剤
によって凝集除去することができる。3,4−ジクロロ
アニリン0.5mM、過酸化水素0.5mM、ペルオキ
シダ−ゼ1U/ml、フェノ−ル0.5mM及びリン酸
緩衝液5mM(pH 7.0)を含有する反応液を室温
でかくはんした。1時間後の3,4−ジクロロアニリン
除去率は100%で、褐色の溶液となったが、沈殿しな
い。この溶液にヘキサメチレンジアミン−エピクロロヒ
ドリン重縮合物1mg/lを添加しかくはんしたとこ
ろ、凝集し、上澄液は無色透明の液となった。
Example 10 Although 3,4-dichloroaniline cannot be catalytically oxidized by peroxidase by itself, it is polymerized with phenol oxide by adding phenol as an auxiliary agent, and this is converted into an amino group. It can be removed by aggregation with the cationic aggregating agent. A reaction liquid containing 0.5 mM of 3,4-dichloroaniline, 0.5 mM of hydrogen peroxide, 1 U / ml of peroxidase, 0.5 mM of phenol, and 5 mM of phosphate buffer (pH 7.0) at room temperature. I stirred it. The removal rate of 3,4-dichloroaniline after 1 hour was 100%, and a brown solution was obtained, but no precipitation occurred. Hexamethylenediamine-epichlorohydrin polycondensate (1 mg / l) was added to this solution and stirred.

【0029】[0029]

【発明の効果】以上説明したようにフェノ−ル類及びア
ニリン類がフェノ−ル酸化酵素で触媒酸化されて生成す
る酸化生成物は、アミノ基を有する陽イオン性凝集剤と
極めて容易に反応する。したがって、フェノ−ル酸化酵
素及びアミノ基を有する陽イオン性凝集剤を併用するこ
とにより、フェノ−ル酸化酵素の失活を防ぎながら、水
中のフェノ−ル類及びアニリン類を酸化し、その生成物
を凝集し、完全に除去することができる。また、酸化生
成物とアミノ基が極めて容易に反応することから、凝集
剤の使用量は少量で十分である。
As described above, the oxidation product produced by the catalytic oxidation of phenols and anilines with phenol oxidase reacts very easily with the cationic flocculant having an amino group. . Therefore, the phenol oxidase and the cationic flocculant having an amino group are used in combination to oxidize the phenols and anilines in water while preventing the inactivation of the phenol oxidase, and to produce the product. It can aggregate and be completely removed. Further, since the oxidation product and the amino group react extremely easily, a small amount of the aggregating agent is sufficient.

フロントページの続き (51)Int.Cl.5 識別記号 庁内整理番号 FI 技術表示箇所 C02F 1/72 Z 9045−4D Continuation of front page (51) Int.Cl. 5 Identification code Office reference number FI technical display location C02F 1/72 Z 9045-4D

Claims (1)

【特許請求の範囲】[Claims] 【請求項1】 水中のフェノ−ル類及び(または)アニ
リン類を除去する方法において、フェノ−ル類及び(ま
たは)アニリン類を含有する水を、フェノ−ル酸化酵素
及びアミノ基を有する陽イオン性凝集剤を併用して処理
することを特徴とする、上記除去方法。
1. A method for removing phenols and / or anilines in water, wherein water containing phenols and / or anilines is treated with phenol oxidase and an amino group-containing positive group. The above-mentioned removal method, which comprises treating with an ionic flocculant in combination.
JP4264284A 1992-09-07 1992-09-07 Method for removing phenols and anilines from water Expired - Lifetime JPH06102200B2 (en)

Priority Applications (1)

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Application Number Priority Date Filing Date Title
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JPH0686998A true JPH0686998A (en) 1994-03-29
JPH06102200B2 JPH06102200B2 (en) 1994-12-14

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JP2005081278A (en) * 2003-09-09 2005-03-31 Univ Nihon Method for adsorption removing phenolic compound using chitosane bead
CN103663831A (en) * 2013-11-18 2014-03-26 青岛文创科技有限公司 Method for treating wastewater containing anilines
CN103693748A (en) * 2013-12-11 2014-04-02 山东华亚环保科技有限公司 Enzyme preparation for treating industrial sewage
CN104860481A (en) * 2015-05-23 2015-08-26 张家港市山牧新材料技术开发有限公司 Method for treating sewage of food enterprise
CN105253969A (en) * 2015-08-31 2016-01-20 蚌埠龙达农业专业合作社 Contamination-reducing nutrient-increasing additive for aquaculture water and preparation method thereof
CN115057540A (en) * 2022-07-06 2022-09-16 吉林大学 Phenol sewage treatment method based on nano enzyme UMP-Cu with laccase activity

Cited By (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2005081278A (en) * 2003-09-09 2005-03-31 Univ Nihon Method for adsorption removing phenolic compound using chitosane bead
CN103663831A (en) * 2013-11-18 2014-03-26 青岛文创科技有限公司 Method for treating wastewater containing anilines
CN103693748A (en) * 2013-12-11 2014-04-02 山东华亚环保科技有限公司 Enzyme preparation for treating industrial sewage
CN103693748B (en) * 2013-12-11 2015-06-10 山东华亚环保科技有限公司 Enzyme preparation for treating industrial sewage
CN104860481A (en) * 2015-05-23 2015-08-26 张家港市山牧新材料技术开发有限公司 Method for treating sewage of food enterprise
CN105253969A (en) * 2015-08-31 2016-01-20 蚌埠龙达农业专业合作社 Contamination-reducing nutrient-increasing additive for aquaculture water and preparation method thereof
CN115057540A (en) * 2022-07-06 2022-09-16 吉林大学 Phenol sewage treatment method based on nano enzyme UMP-Cu with laccase activity
CN115057540B (en) * 2022-07-06 2023-09-15 吉林大学 Phenolic sewage treatment method based on nano enzyme UMP-Cu with laccase activity

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