JP3233226B2 - Purification method of acrylonitrile - Google Patents

Purification method of acrylonitrile

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Publication number
JP3233226B2
JP3233226B2 JP06984392A JP6984392A JP3233226B2 JP 3233226 B2 JP3233226 B2 JP 3233226B2 JP 06984392 A JP06984392 A JP 06984392A JP 6984392 A JP6984392 A JP 6984392A JP 3233226 B2 JP3233226 B2 JP 3233226B2
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JP
Japan
Prior art keywords
acrylonitrile
base
waste liquid
acid
water
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 - Lifetime
Application number
JP06984392A
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Japanese (ja)
Other versions
JPH05230007A (en
Inventor
学 奥村
正治 横幕
照雄 吉田
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.)
Toagosei Co Ltd
Original Assignee
Toagosei Co Ltd
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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、酸を不純物として含有
するアクリロニトリルを効率良く精製する方法に関し、
アクリロニトリルを原料又は溶媒として用いる各種合成
反応を実施した後に発生するアクリロニトリル廃液の精
製方法として有用である。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a method for efficiently purifying acrylonitrile containing an acid as an impurity.
It is useful as a method for purifying acrylonitrile waste liquid generated after performing various synthetic reactions using acrylonitrile as a raw material or a solvent.

【0002】[0002]

【従来の技術】アクリロニトリルは、特異な臭いを有す
る猛毒な化合物であるが、アクリルアミド又は2−アク
リルアミド−2−メチルプロパンスルホン酸、tert−ブ
チルアクリルアミド及びジアセトンアクリルアミド等に
代表される各種アクリルアミド誘導体の重要な合成原料
として利用されている。これらの内のいくつかの化合物
を合成する際、アクリロニトリルは合成原料として必要
な量より過剰に用いられ、かつ他の合成原料又は触媒と
して硫酸等の酸が用いられるため、反応終了後の反応混
合物から目的生成物を除去すると、硫酸又は有機酸等の
酸を不純物として含むアクリロニトリル(以下アクリロ
ニトリル廃液と称す)が残る。このようなアクリロニト
リル廃液を廃棄するには、アクリロニトリルの毒性を減
少させて安全に廃棄処理するために多大の労力及び設備
を要し、又合成原料として使用し得るアクリロニトリル
を高濃度で含有する廃液を廃棄することは、経済的にも
好ましくないので、これを原料として再使用することが
望まれている。しかし、アクリロニトリル廃液を精製す
ることなく、原料として再使用した場合には生成物の純
度が低下する。
2. Description of the Related Art Acrylonitrile is a highly toxic compound having a peculiar smell, and is a compound of various acrylamide derivatives represented by acrylamide or 2-acrylamide-2-methylpropanesulfonic acid, tert-butylacrylamide, diacetone acrylamide and the like. It is used as an important raw material for synthesis. When synthesizing some of these compounds, acrylonitrile is used in excess of the amount required as a raw material for synthesis, and an acid such as sulfuric acid is used as another raw material for synthesis or as a catalyst. When the target product is removed from the mixture, acrylonitrile containing an acid such as sulfuric acid or an organic acid as an impurity (hereinafter referred to as acrylonitrile waste liquid) remains. In order to dispose of such acrylonitrile waste liquid, a great deal of labor and equipment are required to reduce the toxicity of acrylonitrile and safely dispose it, and a waste liquid containing acrylonitrile at a high concentration that can be used as a synthesis raw material is required. Since discarding is not economically desirable, it is desired to reuse it as a raw material. However, when the acrylonitrile waste liquid is reused as a raw material without purification, the purity of the product is reduced.

【0003】アクリロニトリル廃液から精製されたアク
リロニトリルを回収する方法として、特表平2−500
188号公報において、極少量の水を存在させてアクリ
ロニトリル廃液を塩基で中和し、水難溶性の固体である
塩を形成析出させ、これを遠心分離、濾過、沈降等によ
り機械的に分離、除去した後、このようにして粗精製さ
れたアクリロニトリルを蒸留により精製する方法が提案
されている。しかし、上記方法においては、生成した塩
が塩基を取り込み、中和の進行を阻害するため、中和に
必要な理論量以上の塩基を必要とし、かつ中和速度が遅
いという問題がある。また、塩基によっては中和により
生成した塩が粘稠性であり、これが混合槽の壁に付着す
る傾向があるため、連続的な実施は実質上困難となり、
バッチ方式により実施することになる。その結果、中和
に使用される装置は大型化され、又蒸留に際しては、蒸
留工程へ供給されるアクリロニトリルの不純物成分がば
らつくため、最適な運転条件を維持するよう、常に運転
条件をチェックし、変更しなければならないという問題
が生ずる。
[0003] As a method of recovering acrylonitrile purified from acrylonitrile waste liquid, Japanese Patent Application Laid-Open No. Hei 2-500
No. 188, acrylonitrile waste liquid is neutralized with a base in the presence of a very small amount of water to form a salt which is a hardly water-soluble solid, which is mechanically separated and removed by centrifugation, filtration, sedimentation, etc. After that, a method of purifying acrylonitrile thus roughly purified by distillation has been proposed. However, in the above-mentioned method, since the generated salt takes in a base and inhibits the progress of neutralization, there is a problem that a base more than the theoretical amount required for neutralization is required and the neutralization speed is slow. Also, depending on the base, the salt produced by neutralization is viscous and tends to adhere to the walls of the mixing tank, making continuous practice substantially difficult,
It will be implemented by a batch method. As a result, the equipment used for neutralization is increased in size, and at the time of distillation, the impurity components of acrylonitrile supplied to the distillation process vary, so that the operating conditions are constantly checked to maintain the optimum operating conditions, A problem arises that must be changed.

【0004】従って、アクリロニトリル廃液から不純物
である酸を効率よく除去できる精製方法が望まれてい
た。
[0004] Therefore, there has been a demand for a purification method capable of efficiently removing an acid as an impurity from an acrylonitrile waste liquid.

【0005】[0005]

【発明が解決しようとする課題】本発明は、不純物とし
て酸を含有するアクリロニトリル廃液を中和し、生成す
る中和塩を除去することにより、アクリロニトリル廃液
を効率よく精製する方法を提供するものである。
SUMMARY OF THE INVENTION The present invention provides a method for efficiently purifying an acrylonitrile waste liquid by neutralizing an acrylonitrile waste liquid containing an acid as an impurity and removing a generated neutralized salt. is there.

【0006】[0006]

【発明を解決するための手段】本発明者らは上記課題に
ついて鋭意検討した結果、アクリロニトリル廃液を、中
和反応により生成する中和塩が水に可溶な塩基の水溶液
で中和し、アクリロニトリル層と中和塩を含む水層を形
成させ、形成したアクリロニトリル層と水層を液々分離
することにより、中和の進行を円滑にし、かつ生成した
中和塩の分離を容易ならしめることを見いだし、本発明
を完成するに至った。
Means for Solving the Problems As a result of intensive studies on the above problems, the present inventors have neutralized acrylonitrile waste liquid with an aqueous solution of a base in which a neutralization salt formed by the neutralization reaction is soluble in water, and Layer and an aqueous layer containing a neutralized salt, and by separating the formed acrylonitrile layer and the aqueous layer into liquids, the progress of neutralization is facilitated, and the separation of the generated neutralized salt is facilitated. They have found and completed the present invention.

【0007】すなわち、本発明は不純物として酸を含有
するアクリロニトリルと塩基及び水を接触させて、アク
リロニトリル中の酸との中和反応により生成した水可溶
性の塩を含有する水層を形成させた後、当該水層を分離
除去することを特徴とするアクリロニトリルの精製方法
である。
That is, the present invention relates to a method of forming a water layer containing a water-soluble salt formed by a neutralization reaction of acrylonitrile containing an acid as an impurity with a base and water, and the acid in the acrylonitrile. A method for purifying acrylonitrile, comprising separating and removing the aqueous layer.

【0008】以下に、本発明を更に詳細に説明する。本
発明において用いるアクリロニトリル廃液中の酸は、特
に限定されないが、中和塩を水可溶性とすることが容易
であることから、スルホン酸基を有するものが好まし
く、具体的には例えば硫酸及び有機スルホン酸等があ
る。
Hereinafter, the present invention will be described in more detail. The acid in the acrylonitrile waste liquid used in the present invention is not particularly limited, but is preferably one having a sulfonic acid group because it is easy to make the neutralized salt water-soluble, and specifically, for example, sulfuric acid and organic sulfone. Acids and the like.

【0009】本発明において用いる塩基は、アクリロニ
トリル中の酸との中和反応により生成する塩が水に可溶
であれば特に制限はなく、好ましい具体例としてアンモ
ニア、水酸化ナトリウム、水酸化カリウム、炭酸ナトリ
ウム及び炭酸カリウム等がある。これらの塩基の中で
も、アンモニアと水酸化ナトリウムは、安価に入手で
き、しかも効率良く、アクリロニトリル中の酸を中和す
ることができることから、特に好ましい塩基である。
The base used in the present invention is not particularly limited as long as a salt formed by a neutralization reaction with an acid in acrylonitrile is soluble in water. Preferred examples include ammonia, sodium hydroxide, potassium hydroxide, and the like. There are sodium carbonate and potassium carbonate. Among these bases, ammonia and sodium hydroxide are particularly preferable bases because they can be obtained at low cost and can efficiently neutralize the acid in acrylonitrile.

【0010】本発明の精製方法においては、アクリロニ
トリル中の不純物である酸と塩基との中和反応を円滑に
進行させるために、又中和反応により生成する水可溶性
中和塩を、アクリロニトリル層外へ抽出する水層を形成
させるために充分な量の水を、アクリロニトリルと接触
させる必要がある。
In the purification method of the present invention, a water-soluble neutralized salt formed by the neutralization reaction is added to the acrylonitrile layer in order to smoothly progress the neutralization reaction between the acid and the base, which are impurities in acrylonitrile. It is necessary to contact a sufficient amount of water with acrylonitrile to form an aqueous layer to be extracted into acrylonitrile.

【0011】アクリロニトリル廃液と塩基及び水を接触
させる方法には特に限定はなく、例えばアクリロニトリ
ル廃液に、塩基を混合した後又は塩基を混合する時に水
を混合したり(A)、アクリロニトリル廃液と水を混合
した液に塩基を混合したり(B)、予め塩基の水溶液を
調製しておき、この塩基の水溶液をアクリロニトリル廃
液と混合することもできる(C)。これらの方法の中で
は、特に(C)の方法が効率的であり、好ましい。
The method of contacting the acrylonitrile waste liquid with the base and water is not particularly limited. For example, water is mixed with the acrylonitrile waste liquid after mixing the base or when mixing the base (A), or the acrylonitrile waste liquid and water are mixed. A base may be mixed with the mixed solution (B), or an aqueous solution of the base may be prepared in advance, and the aqueous solution of the base may be mixed with the acrylonitrile waste liquid (C). Among these methods, the method (C) is particularly efficient and preferred.

【0012】上記のように、塩基水溶液はアクリロニト
リル廃液との混合前に調製しても良いし、アクリロニト
リル廃液と塩基を混合する時に水を添加して所望の濃度
に調製しても良いが、何れの場合も、添加された塩基と
水からなる塩基水溶液における塩基の好ましい濃度は、
2〜30wt%である。特に好ましい濃度は、用いる塩
基の種類により適宜調整すれば良く、例えばアンモニア
水溶液を用いた場合、5〜10wt%であり、水酸化ナ
トリウム水溶液を用いた場合、10〜20wt%であ
る。濃度が高い塩基水溶液を用いて中和を行うと、中和
の進行が遅く、かつ中和塩が固体として析出し水層を形
成しない恐れがある。逆に濃度が低い塩基水溶液を用い
て中和を行うと、pH測定値が安定せず、中和反応の終
了時点を的確に判断することが困難となる恐れがある。
塩基の使用量は、アクリロニトリル廃液中の酸と当量と
することが最も望ましいが、該当量の0.9〜1.1倍
量の範囲であれば、全く問題なく、本発明の効果を発揮
させることができる。中和に要する時間は、用いる塩基
により異なるが、通常1〜5分である。なお、アクリロ
ニトリル廃液中に酢酸又は有機スルホン酸を存在させる
と、中和が促進され、短時間で中和を終えることができ
る。アクリロニトリル廃液中に存在させる酢酸又は有機
スルホン酸の好ましい添加割合は、アクリロニトリル廃
液の100重量部(以下単に部と略す)当り0.01〜
5部である。0.01部未満では中和促進効果を十分に
発揮させることが困難となる恐れがあり、5部を越えて
添加しても中和促進効果があまり変化せず、むしろ酸不
純分が高くなるため、好ましくない。
As described above, the aqueous base solution may be prepared before mixing with the waste acrylonitrile solution, or may be adjusted to a desired concentration by adding water when mixing the waste acrylonitrile solution with the base. Also in the case of, the preferred concentration of the base in the aqueous base solution consisting of the added base and water is
2 to 30% by weight. A particularly preferable concentration may be appropriately adjusted depending on the type of the base to be used. For example, when an aqueous ammonia solution is used, the concentration is 5 to 10 wt%, and when an aqueous sodium hydroxide solution is used, the concentration is 10 to 20 wt%. When neutralization is performed using a high-concentration aqueous base solution, the progress of the neutralization may be slow, and the neutralized salt may precipitate as a solid and not form an aqueous layer. Conversely, if neutralization is performed using a low-concentration aqueous base solution, the pH measurement value will not be stable, and it may be difficult to accurately determine the end point of the neutralization reaction.
The use amount of the base is most preferably equivalent to the acid in the acrylonitrile waste liquid, but if it is in the range of 0.9 to 1.1 times the corresponding amount, there is no problem and the effects of the present invention are exhibited. be able to. The time required for neutralization varies depending on the base used, but is usually 1 to 5 minutes. If acetic acid or organic sulfonic acid is present in the acrylonitrile waste liquid, neutralization is promoted, and the neutralization can be completed in a short time. The preferred addition ratio of acetic acid or organic sulfonic acid to be present in the acrylonitrile waste liquid is 0.01 to 100 parts by weight (hereinafter simply referred to as "parts") of the acrylonitrile waste liquid.
5 parts. If it is less than 0.01 part, it may be difficult to sufficiently exert the neutralization accelerating effect, and even if it is added in excess of 5 parts, the neutralization accelerating effect does not change much, and the acid impurity content is rather increased. Therefore, it is not preferable.

【0013】アクリロニトリル廃液と塩基及び水とを効
率良く接触させるには、攪拌機を有する混合槽を用いて
もよいし、スタティックミキサー等の管型混合機を用い
てもよい。かくして中和したアクリロニトリル廃液を静
置することにより、アクリロニトリル層の下に、水可溶
性の中和塩を含む水層を形成させ、これを液々分離すれ
ば、酸が除去されたアクリロニトリルを得ることができ
る。
In order to efficiently contact the acrylonitrile waste liquid with the base and water, a mixing tank having a stirrer may be used, or a tubular mixer such as a static mixer may be used. By leaving the neutralized acrylonitrile waste liquid in this manner, an aqueous layer containing a water-soluble neutralized salt is formed below the acrylonitrile layer, and the liquid is separated into liquid to obtain acrylonitrile from which the acid has been removed. Can be.

【0014】本発明の精製方法は、所望により連続方式
でも実施できる。例えば、撹拌機及びpH電極を有する
反応器中に、アクリロニトリル廃液と塩基水溶液を導入
し、これらを充分接触させて中和した後、中和液を静置
用容器に取り出すことにより、水層とアクリロニトリル
層に分離することができる。
The purification method of the present invention can be carried out in a continuous mode, if desired. For example, in a reactor having a stirrer and a pH electrode, an acrylonitrile waste liquid and a base aqueous solution are introduced, and after sufficient contact and neutralization thereof, the neutralized liquid is taken out to a stationary container, whereby an aqueous layer is formed. It can be separated into acrylonitrile layers.

【0015】上記のようにして分離した水層は直接廃液
燃焼設備に供給して燃焼処理することが可能であり、又
水層に含有されるアクリロニトリルを蒸留等により除去
した後、水層の成分を活性汚泥槽等の廃水処理施設で処
理することも可能である。なお、アクリロニトリルの水
への溶解度は常温で約7wt%であるが、本発明の方法
により液々分離した場合、水層のアクリロニトリル濃度
は、溶解している中和塩の影響で多少変化するが、2〜
3wt%であり、水層の廃棄によるアクリロニトリルの
損失を低減できることも本発明の特徴である。
The aqueous layer separated as described above can be directly supplied to a waste liquid combustion facility for combustion treatment. Further, after acrylonitrile contained in the aqueous layer is removed by distillation or the like, the components of the aqueous layer are removed. Can be treated in a wastewater treatment facility such as an activated sludge tank. The solubility of acrylonitrile in water at room temperature is about 7 wt%. However, when liquids are separated by the method of the present invention, the concentration of acrylonitrile in the aqueous layer slightly changes due to the effect of dissolved neutralizing salts. , 2
Another feature of the present invention is that the content of acrylonitrile is 3 wt%, and the loss of acrylonitrile due to disposal of the aqueous layer can be reduced.

【0016】[0016]

【作用】酸を含むアクリロニトリル廃液を少量の水存在
下、塩基で中和し、析出した塩を遠心分離、濾過、沈降
等により機械的に除去する公知の方法では、中和速度が
遅く、モル当量以上の塩基を必要とする。これは中和反
応が塩基固体の表面上で進行し、かつ生成した塩が塩基
固体表面上を覆うためである。本発明のごとく、水可溶
性の中和塩を形成させる塩基と共に、水層を形成するに
足る水を添加した場合には、生成した中和塩は水層に溶
解し、中和は円滑に進行するため、モル当量の塩基で中
和は完結する。また、中和塩を含む水層を液々分離で除
去することにより、遠心分離等の煩瑣な機械的操作は不
要となり、中和塩の除去は極めて容易になる。
The acrylonitrile waste solution containing an acid is neutralized with a base in the presence of a small amount of water, and the precipitated salt is mechanically removed by centrifugation, filtration, sedimentation, or the like. Requires an equivalent or more base. This is because the neutralization reaction proceeds on the surface of the base solid, and the generated salt covers the surface of the base solid. As in the present invention, when water sufficient to form an aqueous layer is added together with a base that forms a water-soluble neutralized salt, the generated neutralized salt dissolves in the aqueous layer, and neutralization proceeds smoothly. Therefore, neutralization is completed with a molar equivalent of base. Further, by removing the aqueous layer containing the neutralized salt by liquid-liquid separation, a complicated mechanical operation such as centrifugal separation becomes unnecessary, and the removal of the neutralized salt becomes extremely easy.

【0017】[0017]

【実施例】以下実施例にて本発明を具体的に説明する。 実施例1 0.2モルの硫酸及び炭素数が4〜7の有機スルホン酸
が混在する0.1モルの有機スルホン酸を含有するアク
リロニトリル廃液1000gに、8wt%アンモニア水
溶液106g(アンモニア0.5モル)を添加し、攪拌
しながらpHを測定した。pHは30秒後に5.8で安
定した。攪拌を止め、静置したところ、約10秒後にア
クリロニトリル層と水層に分離し、液々分離により硫酸
及び有機スルホン酸が除去されたアクリロニトリル97
5gを得た。
EXAMPLES The present invention will be specifically described below with reference to examples. Example 1 To 1000 g of acrylonitrile waste liquid containing 0.1 mol of organic sulfonic acid in which 0.2 mol of sulfuric acid and organic sulfonic acid having 4 to 7 carbon atoms are mixed, 106 g of 8 wt% ammonia aqueous solution (0.5 mol of ammonia ) Was added and the pH was measured with stirring. The pH stabilized at 5.8 after 30 seconds. When the stirring was stopped and the mixture was allowed to stand, it was separated into an acrylonitrile layer and an aqueous layer after about 10 seconds, and acrylonitrile 97 from which sulfuric acid and organic sulfonic acid had been removed by liquid-liquid separation.
5 g were obtained.

【0018】実施例2 塩基水溶液として、アンモニア水溶液に代えて15wt
%水酸化ナトリウム水溶液133g(水酸化ナトリウム
0.5モル)を用いた他は実施例1と同様にアクリロニ
トリル廃液を中和した。pHは3分後に5.5で安定し
た。攪拌を止め、静置したところ、約15秒後にアクリ
ロニトリル層と水層に分離し、液々分離により硫酸及び
有機スルホン酸が除去されたアクリロニトリル955g
を得た。
Example 2 15 wt.
Acrylonitrile waste liquid was neutralized in the same manner as in Example 1 except that 133 g of a 0.1% aqueous sodium hydroxide solution (0.5 mol of sodium hydroxide) was used. The pH stabilized at 5.5 after 3 minutes. When the stirring was stopped and the mixture was allowed to stand, about 15 seconds later, it separated into an acrylonitrile layer and an aqueous layer, and 955 g of acrylonitrile from which sulfuric acid and organic sulfonic acid had been removed by liquid-liquid separation.
I got

【0019】比較例1 アンモニア水溶液を水酸化カルシウム18.5g(0.
25モル)及び水30gに変更した他は実施例1と同様
にアクリロニトリル廃液を中和しようとしたが、pH値
は15分後に2.5まで上昇したものの、その後は変化
せず、中和を短時間に終了することができなかった。
COMPARATIVE EXAMPLE 1 18.5 g of calcium hydroxide was added to an aqueous ammonia solution.
25 mol) and 30 g of water, except that an attempt was made to neutralize the acrylonitrile waste liquid in the same manner as in Example 1. However, although the pH value increased to 2.5 after 15 minutes, the pH value did not change and neutralization was continued. Could not finish in a short time.

【0020】比較例2 アンモニア水溶液を水酸化カルシウム28.0g(0.
38モル)及び水30gに変更した他は実施例1と同様
に実施した。pHは11分後に6.2で安定した。攪拌
を止め、静置したところ、生成した中和塩の一部が混合
槽の壁に付着し、沈降しなかった。
Comparative Example 2 28.0 g of calcium hydroxide was added to an aqueous ammonia solution (0.
38 mol) and 30 g of water, except that the procedure was as in Example 1. The pH stabilized at 6.2 after 11 minutes. When the stirring was stopped and the mixture was allowed to stand, a part of the generated neutralized salt adhered to the wall of the mixing tank and did not settle.

【0021】実施例3 1.3wt%の硫酸及び0.1wt%の酢酸を含有する
アクリロニトリル廃液1000gに、8wt%アンモニ
ア水溶液32gを添加し、攪拌しながらpHを測定した
結果、pHは1分後に5.8で安定した。
Example 3 32 g of an 8 wt% aqueous ammonia solution was added to 1000 g of acrylonitrile waste liquid containing 1.3 wt% of sulfuric acid and 0.1 wt% of acetic acid, and the pH was measured with stirring. Stabilized at 5.8.

【0022】実施例4 1.3wt%の硫酸及び0.1wt%の酢酸を含有する
アクリロニトリル廃液1000gに、15wt%苛性ソ
ーダ水溶液40gを添加し、攪拌しながらpHを測定し
た結果、pHは3分後に5.8で安定した。
Example 4 To 1000 g of acrylonitrile waste liquid containing 1.3 wt% of sulfuric acid and 0.1 wt% of acetic acid, 40 g of a 15 wt% aqueous sodium hydroxide solution was added, and the pH was measured with stirring. Stabilized at 5.8.

【0023】実施例5 攪拌機及び入口管と出口管を備えたガラス反応器を用い
て、本発明を連続的に実施した。反応器は、アクリロニ
トリル廃液及びアンモニア水溶液の導入管、pH電極を
有し、滞留時間は2分である。0.2モルの硫酸及び炭
素数が4〜7の有機スルホン酸が混在する0.1モルの
有機スルホン酸を含有するアクリロニトリル廃液100
0部に対し、8wt%アンモニア水溶液106部の割合
で供給し、攪拌しながらpHを測定した。pHは5.5
〜5.8の範囲で安定であり、中和された液は水層が均
一に分散した状態で流出した。中和塩の反応器内での析
出、器壁への付着はみられなかった。流出した液は静置
することによりアクリロニトリル層と水層に分離し、液
々分離により、硫酸及び有機スルホン酸が除去されたア
クリロニトリルを供給アクリロニトリル廃液1000部
に対し976部得た。
Example 5 The present invention was continuously carried out using a glass reactor equipped with a stirrer and an inlet tube and an outlet tube. The reactor has an inlet tube for the acrylonitrile waste liquid and the aqueous ammonia solution and a pH electrode, and the residence time is 2 minutes. Acrylonitrile waste liquid 100 containing 0.1 mol of organic sulfonic acid mixed with 0.2 mol of sulfuric acid and organic sulfonic acid having 4 to 7 carbon atoms
The solution was supplied at a ratio of 106 parts of an 8 wt% ammonia aqueous solution to 0 parts, and the pH was measured while stirring. pH 5.5
It was stable in the range of 5.8, and the neutralized liquid flowed out in a state where the aqueous layer was uniformly dispersed. No precipitation of the neutralized salt in the reactor or adhesion to the vessel wall was observed. The effluent was allowed to stand to separate into an acrylonitrile layer and an aqueous layer. By liquid-liquid separation, 976 parts of acrylonitrile from which sulfuric acid and organic sulfonic acid had been removed were obtained with respect to 1000 parts of supplied acrylonitrile waste liquid.

【0024】[0024]

【発明の効果】本発明の精製方法は、酸を含むアクリロ
ニトリルを容易に精製することを可能とするものであ
り、所望により連続式でも実施でき、又精製の際に失わ
れるアクリロニトリルの量も極めて少量であるという特
長を有しており、アクリロニトリルの経済的な精製法と
して斯界にもたらす影響は計り知れないものがある。
The purification method of the present invention makes it possible to easily purify acrylonitrile containing an acid. It can be carried out continuously if desired, and the amount of acrylonitrile lost during purification is extremely small. It has the feature of being in a small amount, and has an immeasurable effect on the world as an economical method for purifying acrylonitrile.

───────────────────────────────────────────────────── フロントページの続き (56)参考文献 特表 平2−500188(JP,A) (58)調査した分野(Int.Cl.7,DB名) C07C 253/34 C07C 255/08 ──────────────────────────────────────────────────続 き Continuation of the front page (56) References Special Table Hei 2-500188 (JP, A) (58) Field surveyed (Int. Cl. 7 , DB name) C07C 253/34 C07C 255/08

Claims (1)

(57)【特許請求の範囲】(57) [Claims] 【請求項1】不純物として酸を含有するアクリロニトリ
ルを塩基及び水と接触させて、該塩基とアクリロニトリ
ル中の酸との中和反応により水可溶性の塩を生成させる
と共に該塩を含有する水層を形成させた後、当該水層を
分離除去することを特徴とするアクリロニトリルの精製
方法。
An acrylonitrile containing an acid as an impurity is brought into contact with a base and water to produce a water-soluble salt by a neutralization reaction between the base and the acid in acrylonitrile, and to form an aqueous layer containing the salt. A method for purifying acrylonitrile, comprising separating and removing the aqueous layer after formation.
JP06984392A 1992-02-19 1992-02-19 Purification method of acrylonitrile Expired - Lifetime JP3233226B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP06984392A JP3233226B2 (en) 1992-02-19 1992-02-19 Purification method of acrylonitrile

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP06984392A JP3233226B2 (en) 1992-02-19 1992-02-19 Purification method of acrylonitrile

Publications (2)

Publication Number Publication Date
JPH05230007A JPH05230007A (en) 1993-09-07
JP3233226B2 true JP3233226B2 (en) 2001-11-26

Family

ID=13414496

Family Applications (1)

Application Number Title Priority Date Filing Date
JP06984392A Expired - Lifetime JP3233226B2 (en) 1992-02-19 1992-02-19 Purification method of acrylonitrile

Country Status (1)

Country Link
JP (1) JP3233226B2 (en)

Also Published As

Publication number Publication date
JPH05230007A (en) 1993-09-07

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