JPH0463869B2 - - Google Patents
Info
- Publication number
- JPH0463869B2 JPH0463869B2 JP59163403A JP16340384A JPH0463869B2 JP H0463869 B2 JPH0463869 B2 JP H0463869B2 JP 59163403 A JP59163403 A JP 59163403A JP 16340384 A JP16340384 A JP 16340384A JP H0463869 B2 JPH0463869 B2 JP H0463869B2
- Authority
- JP
- Japan
- Prior art keywords
- catalyst
- water
- reaction
- organic phase
- tank
- 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
Links
- 239000003054 catalyst Substances 0.000 claims description 117
- 238000006243 chemical reaction Methods 0.000 claims description 51
- 239000012074 organic phase Substances 0.000 claims description 50
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims description 49
- 239000010949 copper Substances 0.000 claims description 41
- 238000000034 method Methods 0.000 claims description 37
- VEXZGXHMUGYJMC-UHFFFAOYSA-N Hydrochloric acid Chemical compound Cl VEXZGXHMUGYJMC-UHFFFAOYSA-N 0.000 claims description 36
- 229910052802 copper Inorganic materials 0.000 claims description 28
- 238000003756 stirring Methods 0.000 claims description 20
- 229910052760 oxygen Inorganic materials 0.000 claims description 16
- QQOMQLYQAXGHSU-UHFFFAOYSA-N 2,3,6-Trimethylphenol Chemical compound CC1=CC=C(C)C(O)=C1C QQOMQLYQAXGHSU-UHFFFAOYSA-N 0.000 claims description 15
- QIXDHVDGPXBRRD-UHFFFAOYSA-N 2,3,5-trimethylcyclohexa-2,5-diene-1,4-dione Chemical compound CC1=CC(=O)C(C)=C(C)C1=O QIXDHVDGPXBRRD-UHFFFAOYSA-N 0.000 claims description 10
- 229910001508 alkali metal halide Inorganic materials 0.000 claims description 9
- 150000008045 alkali metal halides Chemical class 0.000 claims description 9
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 claims description 9
- 239000001301 oxygen Substances 0.000 claims description 9
- 239000007864 aqueous solution Substances 0.000 claims description 8
- RYGMFSIKBFXOCR-UHFFFAOYSA-N Copper Chemical compound [Cu] RYGMFSIKBFXOCR-UHFFFAOYSA-N 0.000 claims description 7
- 239000002253 acid Substances 0.000 claims description 7
- 229910052736 halogen Inorganic materials 0.000 claims description 6
- DNIAPMSPPWPWGF-GSVOUGTGSA-N (R)-(-)-Propylene glycol Chemical compound C[C@@H](O)CO DNIAPMSPPWPWGF-GSVOUGTGSA-N 0.000 claims description 5
- 229910052783 alkali metal Inorganic materials 0.000 claims description 5
- 150000001340 alkali metals Chemical class 0.000 claims description 5
- 150000002367 halogens Chemical class 0.000 claims description 5
- QGZKDVFQNNGYKY-UHFFFAOYSA-O Ammonium Chemical compound [NH4+] QGZKDVFQNNGYKY-UHFFFAOYSA-O 0.000 claims description 4
- 125000004432 carbon atom Chemical group C* 0.000 claims description 3
- 238000002425 crystallisation Methods 0.000 claims description 3
- 230000008025 crystallization Effects 0.000 claims description 3
- 239000007789 gas Substances 0.000 claims description 3
- 238000004519 manufacturing process Methods 0.000 claims description 3
- 230000000737 periodic effect Effects 0.000 claims description 3
- 238000010438 heat treatment Methods 0.000 claims description 2
- 238000000605 extraction Methods 0.000 description 50
- -1 halogen ions Chemical class 0.000 description 20
- 239000008346 aqueous phase Substances 0.000 description 19
- 229910021591 Copper(I) chloride Inorganic materials 0.000 description 14
- OXBLHERUFWYNTN-UHFFFAOYSA-M copper(I) chloride Chemical compound [Cu]Cl OXBLHERUFWYNTN-UHFFFAOYSA-M 0.000 description 14
- 239000000243 solution Substances 0.000 description 13
- 239000007788 liquid Substances 0.000 description 12
- KWGKDLIKAYFUFQ-UHFFFAOYSA-M lithium chloride Chemical compound [Li+].[Cl-] KWGKDLIKAYFUFQ-UHFFFAOYSA-M 0.000 description 12
- 238000011084 recovery Methods 0.000 description 9
- 239000005749 Copper compound Substances 0.000 description 8
- 150000001880 copper compounds Chemical class 0.000 description 8
- 230000000694 effects Effects 0.000 description 8
- 239000013078 crystal Substances 0.000 description 7
- 238000001704 evaporation Methods 0.000 description 7
- 229910052792 caesium Inorganic materials 0.000 description 6
- 239000000460 chlorine Substances 0.000 description 6
- 150000002500 ions Chemical class 0.000 description 6
- 239000012071 phase Substances 0.000 description 6
- 229910021589 Copper(I) bromide Inorganic materials 0.000 description 5
- 230000000052 comparative effect Effects 0.000 description 5
- 238000005265 energy consumption Methods 0.000 description 5
- 230000008020 evaporation Effects 0.000 description 5
- 238000001556 precipitation Methods 0.000 description 5
- 239000007787 solid Substances 0.000 description 5
- GVJHHUAWPYXKBD-UHFFFAOYSA-N (±)-α-Tocopherol Chemical compound OC1=C(C)C(C)=C2OC(CCCC(C)CCCC(C)CCCC(C)C)(C)CCC2=C1C GVJHHUAWPYXKBD-UHFFFAOYSA-N 0.000 description 4
- 229910052801 chlorine Inorganic materials 0.000 description 4
- ORTQZVOHEJQUHG-UHFFFAOYSA-L copper(II) chloride Chemical compound Cl[Cu]Cl ORTQZVOHEJQUHG-UHFFFAOYSA-L 0.000 description 4
- ZSIAUFGUXNUGDI-UHFFFAOYSA-N hexan-1-ol Chemical compound CCCCCCO ZSIAUFGUXNUGDI-UHFFFAOYSA-N 0.000 description 4
- 229910052700 potassium Inorganic materials 0.000 description 4
- SQGYOTSLMSWVJD-UHFFFAOYSA-N silver(1+) nitrate Chemical compound [Ag+].[O-]N(=O)=O SQGYOTSLMSWVJD-UHFFFAOYSA-N 0.000 description 4
- ZMXDDKWLCZADIW-UHFFFAOYSA-N N,N-Dimethylformamide Chemical compound CN(C)C=O ZMXDDKWLCZADIW-UHFFFAOYSA-N 0.000 description 3
- 229910001416 lithium ion Inorganic materials 0.000 description 3
- 230000008018 melting Effects 0.000 description 3
- 238000002844 melting Methods 0.000 description 3
- 239000003960 organic solvent Substances 0.000 description 3
- 230000001590 oxidative effect Effects 0.000 description 3
- 238000004062 sedimentation Methods 0.000 description 3
- 239000011949 solid catalyst Substances 0.000 description 3
- 238000004448 titration Methods 0.000 description 3
- WCUXLLCKKVVCTQ-UHFFFAOYSA-M Potassium chloride Chemical compound [Cl-].[K+] WCUXLLCKKVVCTQ-UHFFFAOYSA-M 0.000 description 2
- FAPWRFPIFSIZLT-UHFFFAOYSA-M Sodium chloride Chemical compound [Na+].[Cl-] FAPWRFPIFSIZLT-UHFFFAOYSA-M 0.000 description 2
- 229930003427 Vitamin E Natural products 0.000 description 2
- 238000001479 atomic absorption spectroscopy Methods 0.000 description 2
- 238000010923 batch production Methods 0.000 description 2
- 229910052794 bromium Inorganic materials 0.000 description 2
- LYQFWZFBNBDLEO-UHFFFAOYSA-M caesium bromide Chemical compound [Br-].[Cs+] LYQFWZFBNBDLEO-UHFFFAOYSA-M 0.000 description 2
- AIYUHDOJVYHVIT-UHFFFAOYSA-M caesium chloride Chemical compound [Cl-].[Cs+] AIYUHDOJVYHVIT-UHFFFAOYSA-M 0.000 description 2
- 230000003197 catalytic effect Effects 0.000 description 2
- 239000007795 chemical reaction product Substances 0.000 description 2
- 239000007810 chemical reaction solvent Substances 0.000 description 2
- 239000012141 concentrate Substances 0.000 description 2
- 238000011437 continuous method Methods 0.000 description 2
- 229960003280 cupric chloride Drugs 0.000 description 2
- KSOUCCXMYMQGDF-UHFFFAOYSA-L dichlorocopper;lithium Chemical compound [Li].Cl[Cu]Cl KSOUCCXMYMQGDF-UHFFFAOYSA-L 0.000 description 2
- WIGCFUFOHFEKBI-UHFFFAOYSA-N gamma-tocopherol Natural products CC(C)CCCC(C)CCCC(C)CCCC1CCC2C(C)C(O)C(C)C(C)C2O1 WIGCFUFOHFEKBI-UHFFFAOYSA-N 0.000 description 2
- 229910052500 inorganic mineral Inorganic materials 0.000 description 2
- 229910052744 lithium Inorganic materials 0.000 description 2
- 239000011707 mineral Substances 0.000 description 2
- 239000002244 precipitate Substances 0.000 description 2
- 229910001961 silver nitrate Inorganic materials 0.000 description 2
- JHJLBTNAGRQEKS-UHFFFAOYSA-M sodium bromide Chemical compound [Na+].[Br-] JHJLBTNAGRQEKS-UHFFFAOYSA-M 0.000 description 2
- 239000000126 substance Substances 0.000 description 2
- 229940046009 vitamin E Drugs 0.000 description 2
- 235000019165 vitamin E Nutrition 0.000 description 2
- 239000011709 vitamin E Substances 0.000 description 2
- AUFZRCJENRSRLY-UHFFFAOYSA-N 2,3,5-trimethylhydroquinone Chemical compound CC1=CC(O)=C(C)C(C)=C1O AUFZRCJENRSRLY-UHFFFAOYSA-N 0.000 description 1
- BMYNFMYTOJXKLE-UHFFFAOYSA-N 3-azaniumyl-2-hydroxypropanoate Chemical compound NCC(O)C(O)=O BMYNFMYTOJXKLE-UHFFFAOYSA-N 0.000 description 1
- LXBONPACIOPBAZ-UHFFFAOYSA-N 4-chloro-2,3,5-trimethylphenol Chemical compound CC1=CC(O)=C(C)C(C)=C1Cl LXBONPACIOPBAZ-UHFFFAOYSA-N 0.000 description 1
- MYMOFIZGZYHOMD-UHFFFAOYSA-N Dioxygen Chemical compound O=O MYMOFIZGZYHOMD-UHFFFAOYSA-N 0.000 description 1
- GRYLNZFGIOXLOG-UHFFFAOYSA-N Nitric acid Chemical compound O[N+]([O-])=O GRYLNZFGIOXLOG-UHFFFAOYSA-N 0.000 description 1
- 150000007513 acids Chemical class 0.000 description 1
- SWLVFNYSXGMGBS-UHFFFAOYSA-N ammonium bromide Chemical compound [NH4+].[Br-] SWLVFNYSXGMGBS-UHFFFAOYSA-N 0.000 description 1
- 239000012736 aqueous medium Substances 0.000 description 1
- 238000009835 boiling Methods 0.000 description 1
- 239000013522 chelant Substances 0.000 description 1
- 150000004700 cobalt complex Chemical class 0.000 description 1
- 150000001875 compounds Chemical class 0.000 description 1
- 230000003247 decreasing effect Effects 0.000 description 1
- 229910001882 dioxygen Inorganic materials 0.000 description 1
- 238000009826 distribution Methods 0.000 description 1
- 238000004817 gas chromatography Methods 0.000 description 1
- XMBWDFGMSWQBCA-UHFFFAOYSA-N hydrogen iodide Chemical compound I XMBWDFGMSWQBCA-UHFFFAOYSA-N 0.000 description 1
- 229940071870 hydroiodic acid Drugs 0.000 description 1
- 238000009776 industrial production Methods 0.000 description 1
- 229910052740 iodine Inorganic materials 0.000 description 1
- 239000007791 liquid phase Substances 0.000 description 1
- 239000000463 material Substances 0.000 description 1
- 229910017604 nitric acid Inorganic materials 0.000 description 1
- 238000007254 oxidation reaction Methods 0.000 description 1
- 238000005191 phase separation Methods 0.000 description 1
- 230000000704 physical effect Effects 0.000 description 1
- IOLCXVTUBQKXJR-UHFFFAOYSA-M potassium bromide Chemical compound [K+].[Br-] IOLCXVTUBQKXJR-UHFFFAOYSA-M 0.000 description 1
- 230000001376 precipitating effect Effects 0.000 description 1
- 239000002243 precursor Substances 0.000 description 1
- 229910052701 rubidium Inorganic materials 0.000 description 1
- 239000011780 sodium chloride Substances 0.000 description 1
- 239000002904 solvent Substances 0.000 description 1
Classifications
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02P—CLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
- Y02P20/00—Technologies relating to chemical industry
- Y02P20/50—Improvements relating to the production of bulk chemicals
- Y02P20/52—Improvements relating to the production of bulk chemicals using catalysts, e.g. selective catalysts
Landscapes
- Organic Low-Molecular-Weight Compounds And Preparation Thereof (AREA)
- Low-Molecular Organic Synthesis Reactions Using Catalysts (AREA)
Description
〔産業上の利用分野〕
本発明は触媒の回収方法に関するものであり、
詳しくは2,3,6−トリメチルフエノール(以
下、TMPと略する)を水及び炭素数5〜10の脂
肪族アルコール類中で銅ハロゲノ錯体触媒の存在
下、分子状酸素と接触させて2,3,5−トリメ
チルベンゾキノン(以下、TMBQと略する)を
製造する方法における触媒の回収方法に関するも
のである。
TMBQはビタミンEの合成中間体として有用
な物質である。
〔従来の技術〕
触媒の存在下、TMPを酸素で酸化してTMBQ
を得る方法としては種々の方法が知られている。
例えば、特公昭53−17585号公報は銅及びハロゲ
ンイオンの存在下、TMPを酸素で酸化する方法
を開示し、特公昭49−24465号公報はコバルト錯
体を触媒とする方法を開示している。
これらの方法は限定された条件下ではTMBQ
の収率が高く、優れた方法の一つと考えられる
が、これらの方法が工業的製造法として成立する
には触媒が反応系から容易に回収でき、回収され
た触媒の活性が常に維持されていることが必要で
ある。しかしながら、上記した公報には触媒の回
収は可能であるとの記載はあるものの具体的な回
収方法および回収した触媒の活性についての記載
はない。
例えば特公昭53−17585号公報では水に易溶な
有機溶媒、例えばジメチルホルムアミド中で反応
を行い、反応終了後に大量の水を導入し、次いで
水に不溶な有機溶媒、例えば四塩化炭素で有機物
を抽出して有機相と水相に分離し、分離された水
相は触媒水溶液として次の反応に使用し得るとさ
れている。しかしながら、回収触媒の活性につい
ての言及はなく、また他の実施例によれば水が存
在した系で反応を行つた場合、触媒の活性は低く
極めて効率の悪い反応になつている。したがつ
て、水相に移行した触媒を触媒水溶液としてその
まま用いることは実際上、実施し得ないことであ
る。
それ故に特公昭53−17585号公報においては回
収触媒に十分な触媒活性を発揮させるためには触
媒が移行した触媒水溶液から完全に水を蒸発さ
せ、触媒を固体状で回収し反応に供しなければな
らない。しかしながら、この方法は大量の水を蒸
発させる必要があるためエネルギー消費が大きく
なると同時に反応溶媒と抽出溶媒の分離が必要で
ある等、反応終了後から触媒を回収するまでの過
程が複雑であり、工業的実施に当たつては多くの
困難がある。
特公昭49−24465号公報の方法においても触媒
の回収は可能であろうが上記と同様の理由により
工業的実施に当たつては難点が多いし、更に触媒
寿命が短いという大きな欠点を有する。
本発明者らは先に銅ハロゲノ錯体或いは銅ハロ
ゲノ錯体とアルカリ金属ハロゲン化物からなる触
媒を用い、水および有機溶媒の共存下にTMPを
酸化する方法を提案した。ここで用いる触媒は水
媒体中で使用するものである。またこの方法では
有機溶媒として水に殆ど不溶なC5〜C10の脂肪族
アルコールを用いる。従つて反応は完全な液々不
均一系で行われるが反応は全く問題なく進行し、
また反応終了後、触媒を含む水相と有機相とは容
易に分離でき、したがつて触媒の回収も容易であ
り相分離した触媒液はそのまま反応に供すること
ができる。しかしながら分離された有機相中には
若干量の水と共に触媒が存在しており相分離だけ
では完全な触媒回収はできない。
有機相に存在している触媒量は使用する銅ハロ
ゲノ錯体、アルカリ金属ハロゲン化物の種類、
量、水相における濃度などによつて異なるが、触
媒回収操作を省略することは触媒の大きな損失と
なり好ましくない。
反応後、分離された有機相に存在している触媒
は水により容易に抽出できると考えられる。しか
しながら銅ハロゲノ錯体を反応に使用した場合、
有機相には溶解するが水には殆ど不溶の構造不明
の銅化合物が若干量生成し、水による抽出操作
時、水相及び有機相のいずれかの相にもそれが微
細な結晶として析出する。結局、抽出操作後でも
有機相に銅が存在し、不完全な抽出となる。この
場合、デカンターなどにより該銅化合物を沈降さ
せ固液の分離を行い抽出操作を続行することが考
えられるが、操作が煩雑であるばかりでなく分離
した構造不明の銅化合物を再び触媒として用いる
ことの妥当性に問題があり、また一方、それを廃
棄することは触媒の損失となるので好ましくな
い。
〔発明が解決しようとする問題点〕
従つて触媒の活性に全く影響を与えず触媒を簡
潔な操作により抽出し得る有効な触媒の回収法が
必要とされる。
〔問題点を解決するための手段〕
本発明は以上の観点にかんがみてなされたもの
であり、銅ハロゲノ錯体または銅ハロゲノ錯体と
アルカリ金属ハロゲン化物を触媒とし酸素により
TMPを酸化しTMBQを得る反応において、反応
後、分離された有機相より触媒を回収する方法と
してPHを1.5〜2.5に保つて水により触媒を抽出
し、ついで抽出液中の水を蒸発すれば構造不明の
銅化合物の析出もなく又、触媒活性を損なうこと
もなく極めて容易に、且つエネルギー消費も少な
く触媒を回収できるという知見に基づくものであ
る。
本願発明は一般式
Ml〔Cu()mXn〕p
(結晶水を含んでも含まなくてもよい)〔式中、
Mは周期律表においてIAで表されるアルカリ金
属またはアンモニウム、Cu()は二価の銅、X
はハロゲン、lは1〜3の整数、mは1または
2、nは3〜8の整数、pは1または2〕
で示される銅ハロゲノ錯体、又は該銅ハロゲノ錯
体とアルカリ金属ハロゲン化物からなる触媒を用
いて水及び炭素数5〜10の脂肪族アルコール中で
2,3,6−トリメチルフエノールを酸素又は酸
素含有ガスと接触させ2,3,5−トリメチルベ
ンゾキノンを製造する方法において、
反応後、分液された有機相より水を用い、抽出
装置内のPHを1.5〜2.5に保ちながら触媒を抽出
し、次いで抽出液内の水を蒸発させて触媒を回収
することを特徴とする触媒の回収方法に関するも
のである。
本発明において用いられる銅ハロゲノ錯体は銅
とハロゲンが配位結合をした化合物、すなわち一
般式Ml〔Cu()mXn〕p
(式中、Mは周期律表においてIAで表されるア
ルカリ金属またはアンモニウム、Cu()は二価
の銅、Xはハロゲン、lは1〜3の整数、mは1
または2、nは3〜8の整数、pは1または2、
l+2mp=np)
で示される化合物(結晶水を含んでも含まなくて
もよい)である。
上記式においてMとしてはアルカリ金属、アン
モニウムが好ましく、アルカリ金属としてはLi、
K、Rb、Cs、好ましくはLi、K、Cs、特に好ま
しくはLiがあげられる。またハロゲンとしては
Cl、Br、Iが好ましく、特にCl、Brが好ましい。
銅ハロゲノ錯体としては例えば、Li〔CuCl3〕・
2H2O、NH4〔CuCl3〕・2H2O、(NH4)2〔CuCl4〕・
2H2O、K〔CuCl3〕、K2〔CuCl4〕・2H2O、Cs
〔CuCl3〕・2H2O、Cs2〔CuCl4〕・2H2O、Cs3
〔Cu2Cl7〕・2H2O.Li2〔CuBr4〕・6H2O、K
〔CuBr3〕、(NH4)2〔CuBr4〕・2H2O、Cs2
〔CuBr4〕、Cs〔CuBr3〕などがあげられる。これ
らの銅ハロゲノ錯体は公知方法、例えば
Mellor′s Comprehensive Treatment on
Inorganic and Theoretical Chemistry、Vol
、p182〜201(Longman)により合成すること
ができる。
このようにして合成した銅ハロゲノ錯体は融点
の測定などによつて同定できる。例えば、合成し
た塩化銅リチウム錯体Li〔CuCl3〕・2H2Oは赤褐
色を呈しており、塩化第二銅CuCl2・2H2Oの緑
色の結晶とは外観において全く異なり、その融点
は130〜135℃を示す。塩化銅リチウムLi
〔CuCl3〕・2H2O、塩化第二銅CuCl2・2H2Oの融
点は文献(Mellor′s Comprehensive Treatment
on Inorganic and Theoretical Chemistry,
Vol、p184、p169(Longman)によればそれぞ
れ、130℃、110℃である。
アルカリ金属ハロゲン化物はNaCl、LiCl、
KCl、CsCl、NaBr、NH4Br、KBr、CsBr、
Nai、LiI、KI、CsIなどであり、特にLiClの使用
が好ましい。
本発明における触媒回収は例えば第1図に示し
たような流れによつて達成される。第1図に示し
たように、反応後、液液分離され有機相と水相に
分離される。有機相は水(および酸、例えば塩
酸)で抽出され、有機相と水相に分離され、触媒
を含む水相は反応液の抽出により得られた水相と
一緒に濃縮され触媒が回収される。かくして回収
された触媒は次回の反応に使用される。
本発明において反応は銅ハロゲノ錯体或いは銅
ハロゲノ錯体とアルカリ金属ハロゲン化物からな
る触媒を用いて行われる。反応は反応溶媒として
C5〜C10の脂肪族アルコールを用い、回分式或い
はTMP溶液を触媒水溶液に滴下する半回分式反
応で行われる。使用する触媒量は標準的な条件で
は回分式反応ではTMP/Me〔Cu()mXn〕
p/MX(モル比)=1/1/2〜1/1/4、半
回分式反応ではTMP/Ml〔Cu()mXn〕p/
MX(モル比)=1/0.25/0.5〜1/0.25/1であ
る。
反応後、触媒相である水相と反応生成物等を含
む有機相は容易に分離される。
相分離された有機相中には前述したような標準
的な半回分式の反応の場合を例にとると銅ハロゲ
ノ錯体は1〜5wt%、アルカリ金属ハロゲン化物
は0.5〜2wt%存在する。
分液された有機相からの触媒の抽出は種々の方
式で可能であるが、有機相から完全に触媒を回収
する必要があること、触媒液が腐食性を有するの
で簡単な形式、構造の抽出装置であることが望ま
しい。これらの点から最も好ましい装置として考
えられるのは各撹拌槽の間に沈降槽を有する向流
多段型の抽出装置である。
第2図は向流多段抽出装置を用いた抽出の流れ
図を例示したものである。第2図において1,
2,3はそれぞれ第1、第2、第3撹拌槽を、
4,5,6はそれぞれ第1、第2、第3沈降槽を
示す。有機相は第1撹拌槽および第2撹拌槽にお
いて塩酸を含む水溶液で向流多段抽出され最終的
には第3撹拌槽において水で抽出され、第3沈降
槽において分離され抜き出される。第3撹拌槽に
供給された水は有機槽を抽出後、分離されて第2
撹拌槽に供給され第2撹拌槽において塩酸によつ
てPH調整され、有機相を抽出し、第2沈降槽で分
離される。ここで分離された水相は第1撹拌槽に
供給され第1撹拌槽においてPH調整され、有機相
を抽出し、第1沈降槽で分離され、抽出液(触媒
を含む水相)として抜き出される。
本発明の有機相からの触媒の抽出においては抽
出装置としては前述したように向流多段撹拌槽の
使用が最も好ましい。さらに用いる槽の数が少な
い程、工業的実施に当たつては経済的であり好ま
しい。槽の数は抽出槽(撹拌槽)入口での触媒の
存在量(反応の実施態様によつて触媒存在量は変
わる)、用いる抽出水量、各槽での有機相の滞留
時間などにより影響されるため一概に決定するこ
とはできないが通常、2〜5槽必要とする。
本発明の有機槽からの触媒の抽出において使用
する抽出水はできるだけ少ない方が後の工程であ
る濃縮操作においてエネルギー消費が少ないこと
から好ましい。しかしながら、使用する抽出水が
あまりにも少ない時は例えば抽出槽に入つてくる
抽出液中の触媒濃度が高いため分配率が低下し抽
出が実際上不可能になつたり、或いは抽出槽の数
を増やす必要が生じたりする。従つて、用いる抽
出水の量には操作上と経済性の面から最適な量が
存在し、有機相に対して20〜30wt%の抽出水、
半回分式の反応を行つた場合には10〜20wt%の
抽出水を用いるのが好ましい。
本発明における有機相からの触媒の抽出におい
ては反応が回分式、半回分式のいずれの方法で行
われても、水による触媒抽出時に微細な結晶が析
出して事実上、抽出操作は不可能となる。この結
晶の構造、物性などは全く明らかではないが鉱酸
類には極めて易溶な物質である。したがつて抽出
操作を円滑に行うには析出した結晶を溶解する方
法が妥当と考えられる。しかしながら使用する鉱
酸は触媒を不活性化しないことが必要であり、そ
の面からハロゲン化水素酸、具体的には塩酸、臭
化水素酸、ヨウ化水素酸の使用が好ましく、特に
塩酸が有効である。
本発明における有機相からの触媒の抽出におい
ては抽出時に析出する微細な結晶を溶解するのに
塩酸の使用が最も好ましい。しかしながら結晶を
溶解するのに足る量以上に塩酸を過剰に加えた場
合には遊離の塩酸が触媒液中に残り反応に不都合
を生ずる。即ち遊離の塩酸を含む触媒液を反応に
用いた場合には反応生成物中に4−クロル−トリ
メチルフエノール(以下、Cl−TMPと省略)が
多くなり、TMBQの収率が低下したり酸化反応
速度が小さくなつたりするので好ましくない。
又、このことを避けるために触媒液中から遊離の
塩酸を除去しようとする場合には触媒液を蒸発乾
固し触媒を固体として取出さなければならない。
この操作は水の蒸発のために多大のエネルギーを
必要とすること、蒸発器からの固体状触媒の取り
出しの煩雑なこと、などから好ましい実施態様で
はない。
したがつてハロゲン化水素酸例えば塩酸の添加
量は厳密に制御する必要があるが、それはPHの制
御によつて容易に行える。PHの制御範囲は1.5〜
2.5であり、この範囲での制御により極めて円滑
な抽出操作が可能であり、触媒の活性を損なうこ
となく触媒の抽出を行うことができる。
抽出槽内のPHを制御するためにはPHコントロー
ラーを用い、これにより定量ポンプを作動させ槽
内に塩酸水溶液を供給するのが好ましい実施態様
である。
本発明における有機相からの触媒の抽出に用い
る塩酸の濃度はあまりにも濃度が低い場合には後
の工程の濃縮において蒸発すべき水の量が多くな
つて好ましくなく、又、濃度が高過ぎると抽出槽
内においてTMBQを分解したり、水溶性銅化合
物との部分的な反応しか起こらないため好ましく
ない。塩酸の濃度としては1〜10wt%が好まし
く、特に好ましくは3〜6wt%である。
本発明における有機相からの触媒の抽出におい
て各抽出槽における有機相の滞留時間は、抽出効
率、水不溶性銅化合物と塩酸との反応等のための
重要な因子の一つである。有機相の滞留時間は第
1相では通常10〜60分、好ましくは20〜40分、第
2槽以降では通常5〜30分、好ましくは10〜20分
である。また沈降槽での滞留時間は有機相と水相
とを合わせた液に関して通常10〜60分、好ましく
は20〜50分である。
本発明において反応が銅ハロゲノ錯体或いは銅
ハロゲノ錯体とアルカリ金属ハロゲン化物を触媒
として行われ、反応後の有機相からの触媒の抽出
操作が好ましい実施態様で行われた場合には、抽
出操作後、得られる有機相に残存する触媒は通常
Cu()イオン換算で10ppm以下、Liイオン換算
で1ppm以下であり、又、触媒の回収率はほぼ100
%であり、極めて効率よく触媒の抽出が行われ
る。
本発明において有機相から抽出された触媒を含
む水溶液は次いで反応直後に分離された触媒水溶
液と合わせ所定の濃度まで濃縮するか、或いは触
媒を含む抽出液から完全に水を蒸発させ固体状触
媒を回収する。前者の方法は連続法での操作が可
能であり、したがつて操作も容易であり又反応時
に発生した水の除去も同時に行なえるので有利で
ある。後者の方法はいわゆる蒸発乾固法である
が、回分式法にならざるを得ないこと、蒸発装置
内から固体状の触媒を取り出すことが困難である
等、取り扱いに難があること、又反応時に発生し
た水を除去するためにさらに別個の蒸発装置を必
要とするなどの欠点を有する。
本発明における触媒液からの水の蒸発に際して
は水溶液における触媒の濃度が高いため沸点上昇
が激しい。したがつて減圧下での蒸発が有利であ
ると考えられるが、蒸発温度をあまりにも低く設
定すると真空度をあげることとなり、その結果と
して加熱エネルギーは低下するものの真空発生装
置としてスチームエジエクターの採用などが必要
となり、エネルギー消費量はかえつて増す結果と
なる。又、触媒液は腐食性が強いので蒸発装置の
材料選定の上からも装置内の温度はできるだけ低
い方が好ましい。したがつて触媒からの水の蒸発
操作条件はエネルギー消費の点と腐食性の両面か
ら決定され蒸発装置内の真空度は通常50〜400mm
Hg、好ましくは50〜200mmHgとする。この時の
蒸発缶内の触媒液の温度は約50〜90℃である。
本発明における触媒からの水の蒸発は回分法、
連続法のいずれの方法でも実施可能であるが、操
作の容易性、安定した触媒濃度で触媒濃縮液が得
られることなどから連続法が好ましい実施態様で
ある。
〔作用および効果〕
本発明によれば反応後、有機相に存在する銅ハ
ロゲノ錯体或いは銅ハロゲノ錯体とアルカリ金属
ハロゲン化物からなる触媒を、その活性を損なう
ことなく、また、触媒の損失なく容易に実施でき
る。また、得られた抽出液は反応後、有機相と分
離して得られた水相と合わせて水を蒸発させるこ
とによつて触媒濃縮液を得ることができ、これは
そのまま次の反応に使用できる。
また触媒の抽出操作によつて得られた有機相は
Cu()イオン換算で10ppm以下、Liイオン換算
で1ppm以下の触媒しか含まず、そのまま還元す
ることによりビタミンEの前駆体である高純度の
2,3,5−トリメチルヒドロキノンを得ること
ができる。
〔実施例〕
以下、本発明を実施例、比較例によつて更に詳
しく説明する。なお、実施例、比較例における反
応率、収率はモル基準で表す。
参考例 1
1の四ツ口フラスコに銅ハロゲノ錯体Li
〔CuCl3〕・2H2O44.6g、塩化リチウム31.8g、水
99.2g、n−ヘキサノール80gを入れ950rpmで
撹拌した。この時の触媒濃度(Li〔CuCl3〕+
LiCl)は39.2wt%であつた。反応系内を40%酸素
濃度のガスで置換し、50℃に加温した。ついで
TMPの30%ヘキサノール溶液460gを4時間で定
量的に滴下した。消費された酸素は逐次、酸素ホ
ルダーにより供給した。
反応終了後、有機相と水相(触媒相)とに分離
した。得られた有機相を水洗浄後、ガスクロマト
グラフイーにより分析した。その結果を参考例1
とし第1表に示す。
[Industrial Application Field] The present invention relates to a catalyst recovery method,
Specifically, 2,3,6-trimethylphenol (hereinafter abbreviated as TMP) is brought into contact with molecular oxygen in water and an aliphatic alcohol having 5 to 10 carbon atoms in the presence of a copper halogeno complex catalyst. The present invention relates to a method for recovering a catalyst in a method for producing 3,5-trimethylbenzoquinone (hereinafter abbreviated as TMBQ). TMBQ is a substance useful as a synthetic intermediate for vitamin E. [Prior art] In the presence of a catalyst, TMP is oxidized with oxygen to form TMBQ
Various methods are known for obtaining .
For example, Japanese Patent Publication No. 53-17585 discloses a method of oxidizing TMP with oxygen in the presence of copper and halogen ions, and Japanese Patent Publication No. 49-24465 discloses a method using a cobalt complex as a catalyst. These methods are limited under limited conditions to TMBQ
However, in order for these methods to be viable as industrial production methods, the catalyst must be easily recovered from the reaction system and the activity of the recovered catalyst must be maintained at all times. It is necessary to be present. However, although the above-mentioned publication states that the catalyst can be recovered, there is no description of a specific recovery method or the activity of the recovered catalyst. For example, in Japanese Patent Publication No. 53-17585, the reaction is carried out in an organic solvent that is easily soluble in water, such as dimethylformamide. is extracted and separated into an organic phase and an aqueous phase, and the separated aqueous phase can be used as an aqueous catalyst solution in the next reaction. However, there is no mention of the activity of the recovered catalyst, and according to other examples, when the reaction is carried out in a system where water is present, the activity of the catalyst is low and the reaction is extremely inefficient. Therefore, it is practically impossible to use the catalyst transferred to the aqueous phase as it is as an aqueous catalyst solution. Therefore, in Japanese Patent Publication No. 53-17585, in order for the recovered catalyst to exhibit sufficient catalytic activity, water must be completely evaporated from the aqueous catalyst solution to which the catalyst has migrated, and the catalyst must be recovered in a solid state and subjected to the reaction. It won't happen. However, this method requires evaporation of a large amount of water, resulting in high energy consumption, and the process from the end of the reaction to the recovery of the catalyst is complicated, such as the need to separate the reaction solvent and extraction solvent. There are many difficulties in industrial implementation. The method disclosed in Japanese Patent Publication No. 49-24465 may also be able to recover the catalyst, but for the same reasons as mentioned above, there are many difficulties in industrial implementation, and it also has the major drawback of short catalyst life. The present inventors previously proposed a method of oxidizing TMP in the coexistence of water and an organic solvent using a catalyst consisting of a copper halide complex or a copper halide complex and an alkali metal halide. The catalyst used here is one used in an aqueous medium. Further, in this method, a C5 to C10 aliphatic alcohol, which is almost insoluble in water, is used as an organic solvent. Therefore, although the reaction takes place in a completely liquid-liquid heterogeneous system, the reaction proceeds without any problems.
Further, after the reaction is completed, the aqueous phase containing the catalyst and the organic phase can be easily separated, and therefore the catalyst can be easily recovered, and the phase-separated catalyst liquid can be directly used for the reaction. However, the catalyst is present in the separated organic phase along with a small amount of water, and complete catalyst recovery cannot be achieved by phase separation alone. The amount of catalyst present in the organic phase depends on the type of copper halide complex and alkali metal halide used,
Although it varies depending on the amount, concentration in the aqueous phase, etc., omitting the catalyst recovery operation is not preferable because it results in a large loss of the catalyst. It is believed that after the reaction, the catalyst present in the separated organic phase can be easily extracted with water. However, when a copper halide complex is used in the reaction,
A small amount of a copper compound of unknown structure that is soluble in the organic phase but almost insoluble in water is produced, and during extraction with water, it precipitates as fine crystals in either the aqueous phase or the organic phase. . As a result, copper is present in the organic phase even after the extraction operation, resulting in incomplete extraction. In this case, it may be possible to continue the extraction operation by precipitating the copper compound using a decanter or the like to separate the solid and liquid, but this is not only complicated, but also requires the use of the separated copper compound of unknown structure as a catalyst again. There is a problem with the validity of the catalyst, and on the other hand, it is not preferable to discard it because it will result in a loss of catalyst. [Problems to be Solved by the Invention] Therefore, there is a need for an effective catalyst recovery method that can extract the catalyst through simple operations without affecting the activity of the catalyst at all. [Means for Solving the Problems] The present invention has been made in view of the above-mentioned points of view.
In the reaction of oxidizing TMP to obtain TMBQ, a method for recovering the catalyst from the separated organic phase after the reaction is to extract the catalyst with water while keeping the pH between 1.5 and 2.5, and then evaporate the water in the extract. This method is based on the knowledge that the catalyst can be recovered very easily and with low energy consumption without precipitation of copper compounds of unknown structure and without impairing the catalytic activity. The present invention is based on the general formula Ml[Cu()mXn]p (which may or may not contain water of crystallization) [in the formula,
M is an alkali metal or ammonium represented by IA in the periodic table, Cu () is divalent copper, X
is a halogen, l is an integer of 1 to 3, m is 1 or 2, n is an integer of 3 to 8, p is 1 or 2], or the copper halogeno complex and an alkali metal halide. In a method for producing 2,3,5-trimethylbenzoquinone by contacting 2,3,6-trimethylphenol with oxygen or an oxygen-containing gas in water and an aliphatic alcohol having 5 to 10 carbon atoms using a catalyst, after the reaction. , the catalyst is extracted from the separated organic phase using water while maintaining the pH in the extractor at 1.5 to 2.5, and then the water in the extract is evaporated to recover the catalyst. This concerns the collection method. The copper halide complex used in the present invention is a compound in which copper and halogen have a coordinate bond, that is, the general formula Ml[Cu()mXn]p (where M is an alkali metal or ammonium represented by IA in the periodic table). , Cu() is divalent copper, X is halogen, l is an integer from 1 to 3, m is 1
or 2, n is an integer from 3 to 8, p is 1 or 2,
l+2mp=np) (which may or may not contain water of crystallization). In the above formula, M is preferably an alkali metal or ammonium, and the alkali metals are Li,
K, Rb, Cs, preferably Li, K, Cs, particularly preferably Li. Also, as a halogen
Cl, Br, and I are preferred, and Cl and Br are particularly preferred.
Examples of copper halide complexes include Li[CuCl 3 ].
2H 2 O, NH 4 [CuCl 3 ]・2H 2 O, (NH 4 ) 2 [CuCl 4 ]・
2H 2 O, K [CuCl 3 ], K 2 [CuCl 4 ]・2H 2 O, Cs
[CuCl 3 ]・2H 2 O, Cs 2 [CuCl 4 ]・2H 2 O, Cs 3
[Cu 2 Cl 7 ]・2H 2 O.Li 2 [CuBr 4 ]・6H 2 O, K
[CuBr 3 ], (NH 4 ) 2 [CuBr 4 ]・2H 2 O, Cs 2
Examples include [CuBr 4 ] and Cs[CuBr 3 ]. These copper halide complexes can be prepared by known methods, e.g.
Mellor's Comprehensive Treatment on
Inorganic and Theoretical Chemistry, Vol.
, p182-201 (Longman). The copper halide complex synthesized in this manner can be identified by measuring its melting point. For example, the synthesized copper chloride lithium complex Li[CuCl 3 ].2H 2 O has a reddish-brown color, which is completely different in appearance from the green crystals of cupric chloride CuCl 2.2H 2 O, and its melting point is 130 ~ Indicates 135℃. Copper chloride lithium Li
[CuCl 3 ]・2H 2 O, the melting point of cupric chloride CuCl 2・2H 2 O is given in the literature (Mellor's Comprehensive Treatment
on Inorganic and Theoretical Chemistry,
According to Vol, p184, p169 (Longman), it is 130℃ and 110℃, respectively. Alkali metal halides include NaCl, LiCl,
KCl, CsCl, NaBr, NH4Br , KBr, CsBr,
Nai, LiI, KI, CsI, etc., with LiCl being particularly preferred. Catalyst recovery in the present invention is achieved, for example, by the flow shown in FIG. As shown in FIG. 1, after the reaction, the liquid is separated into an organic phase and an aqueous phase. The organic phase is extracted with water (and acid, e.g. hydrochloric acid) and separated into organic and aqueous phases, and the aqueous phase containing the catalyst is concentrated together with the aqueous phase obtained by extraction of the reaction solution to recover the catalyst. . The catalyst thus recovered is used for the next reaction. In the present invention, the reaction is carried out using a catalyst comprising a copper halide complex or a copper halide complex and an alkali metal halide. The reaction is carried out as a reaction solvent.
The reaction is carried out using a C 5 to C 10 aliphatic alcohol in a batch process or in a semi-batch process in which a TMP solution is added dropwise to an aqueous catalyst solution. Under standard conditions, the amount of catalyst used is TMP/Me[Cu()mXn] for batch reactions.
p/MX (molar ratio) = 1/1/2 to 1/1/4, in semi-batch reaction TMP/Ml[Cu()mXn]p/
MX (molar ratio) = 1/0.25/0.5 to 1/0.25/1. After the reaction, the aqueous phase as the catalyst phase and the organic phase containing the reaction products are easily separated. In the case of the standard semi-batch reaction described above, the copper halide complex is present in the phase-separated organic phase in an amount of 1 to 5 wt%, and the alkali metal halide is present in an amount of 0.5 to 2 wt%. Extraction of the catalyst from the separated organic phase is possible using various methods, but it is necessary to completely recover the catalyst from the organic phase, and since the catalyst liquid is corrosive, it is possible to extract the catalyst in a simple format and structure. Preferably a device. From these points of view, the most preferable device is a countercurrent multi-stage extraction device having a settling tank between each stirring tank. FIG. 2 illustrates a flowchart of extraction using a countercurrent multi-stage extraction device. In Figure 2, 1,
2 and 3 are the first, second and third stirring tanks, respectively.
4, 5, and 6 indicate the first, second, and third sedimentation tanks, respectively. The organic phase is subjected to multistage countercurrent extraction with an aqueous solution containing hydrochloric acid in a first stirring tank and a second stirring tank, and finally extracted with water in a third stirring tank, and separated and extracted in a third settling tank. The water supplied to the third stirring tank is separated after extracting the organic tank and is then sent to the second stirring tank.
It is supplied to a stirring tank, the pH is adjusted with hydrochloric acid in a second stirring tank, the organic phase is extracted, and it is separated in a second settling tank. The aqueous phase separated here is supplied to the first stirring tank, where the pH is adjusted, the organic phase is extracted, separated in the first settling tank, and extracted as an extract (aqueous phase containing the catalyst). It will be done. In the extraction of the catalyst from the organic phase of the present invention, it is most preferable to use a countercurrent multistage stirring tank as the extraction device as described above. Furthermore, the smaller the number of tanks used, the more economical and preferable it is in industrial implementation. The number of tanks is influenced by the amount of catalyst present at the entrance of the extraction tank (stirred tank) (the amount of catalyst varies depending on the method of reaction), the amount of extraction water used, the residence time of the organic phase in each tank, etc. Therefore, it cannot be determined unconditionally, but usually 2 to 5 tanks are required. It is preferable that the amount of extraction water used in the extraction of the catalyst from the organic tank of the present invention is as small as possible, since this reduces energy consumption in the subsequent concentration operation. However, when the amount of extraction water used is too small, for example, the concentration of catalyst in the extract entering the extraction tank may be high, which reduces the distribution ratio and makes extraction practically impossible, or the number of extraction tanks may be increased. The need may arise. Therefore, there is an optimal amount of extraction water to be used from the operational and economic aspects, and 20 to 30 wt% of extraction water to the organic phase,
When carrying out a semi-batch reaction, it is preferable to use 10 to 20 wt% of extraction water. In the extraction of the catalyst from the organic phase in the present invention, whether the reaction is carried out in a batch or semi-batch manner, fine crystals precipitate when the catalyst is extracted with water, making the extraction operation virtually impossible. becomes. Although the structure and physical properties of this crystal are not clear at all, it is a substance that is extremely easily soluble in mineral acids. Therefore, in order to perform the extraction operation smoothly, it is considered appropriate to dissolve the precipitated crystals. However, it is necessary that the mineral acid used does not inactivate the catalyst, and from this point of view it is preferable to use hydrohalic acid, specifically hydrochloric acid, hydrobromic acid, and hydroiodic acid. Hydrochloric acid is particularly effective. It is. In the extraction of the catalyst from the organic phase in the present invention, it is most preferable to use hydrochloric acid to dissolve fine crystals precipitated during extraction. However, if an excessive amount of hydrochloric acid is added in excess of an amount sufficient to dissolve the crystals, free hydrochloric acid remains in the catalyst solution, causing problems in the reaction. That is, when a catalyst solution containing free hydrochloric acid is used in the reaction, a large amount of 4-chloro-trimethylphenol (hereinafter abbreviated as Cl-TMP) will be present in the reaction product, leading to a decrease in the yield of TMBQ and to the oxidation reaction. This is not preferable because the speed may decrease.
Furthermore, in order to avoid this problem, if free hydrochloric acid is to be removed from the catalyst liquid, the catalyst liquid must be evaporated to dryness and the catalyst must be taken out as a solid.
This operation is not a preferred embodiment because it requires a large amount of energy to evaporate water, and it is complicated to take out the solid catalyst from the evaporator. Therefore, it is necessary to strictly control the amount of hydrohalic acid, such as hydrochloric acid, which can be easily controlled by controlling the pH. PH control range is 1.5~
2.5, and by controlling within this range, extremely smooth extraction operation is possible, and the catalyst can be extracted without impairing the activity of the catalyst. In a preferred embodiment, a PH controller is used to control the PH in the extraction tank, and the metering pump is operated by the PH controller to supply an aqueous hydrochloric acid solution into the tank. In the present invention, if the concentration of hydrochloric acid used to extract the catalyst from the organic phase is too low, the amount of water to be evaporated in the subsequent concentration step will increase, which is undesirable. This is undesirable because it decomposes TMBQ in the extraction tank and causes only a partial reaction with water-soluble copper compounds. The concentration of hydrochloric acid is preferably 1 to 10 wt%, particularly preferably 3 to 6 wt%. In the extraction of the catalyst from the organic phase in the present invention, the residence time of the organic phase in each extraction tank is one of the important factors for extraction efficiency, reaction of water-insoluble copper compound and hydrochloric acid, etc. The residence time of the organic phase is usually 10 to 60 minutes, preferably 20 to 40 minutes in the first phase, and usually 5 to 30 minutes, preferably 10 to 20 minutes in the second and subsequent tanks. The residence time in the settling tank is usually 10 to 60 minutes, preferably 20 to 50 minutes for the combined organic phase and aqueous phase. In the present invention, when the reaction is carried out using a copper halide complex or a copper halide complex and an alkali metal halide as a catalyst, and the extraction operation of the catalyst from the organic phase after the reaction is carried out in a preferred embodiment, after the extraction operation, The catalyst remaining in the resulting organic phase is usually
It is less than 10ppm in terms of Cu () ions and less than 1ppm in terms of Li ions, and the recovery rate of the catalyst is almost 100.
%, and the catalyst is extracted extremely efficiently. In the present invention, the aqueous solution containing the catalyst extracted from the organic phase is then combined with the aqueous catalyst solution separated immediately after the reaction and concentrated to a predetermined concentration, or the solid catalyst is removed by completely evaporating water from the extract containing the catalyst. to recover. The former method is advantageous because it can be operated continuously and is therefore easy to operate, and water generated during the reaction can be removed at the same time. The latter method is the so-called evaporation to dryness method, but it has to be a batch method, has difficulties in handling, such as difficulty in taking out the solid catalyst from the evaporator, and is difficult to handle. Disadvantages include the need for a separate evaporator to remove the water generated. When water is evaporated from the catalyst liquid in the present invention, the boiling point rises rapidly because the concentration of the catalyst in the aqueous solution is high. Therefore, evaporation under reduced pressure is considered to be advantageous, but if the evaporation temperature is set too low, the degree of vacuum will increase, and as a result, although the heating energy will decrease, it is not possible to use a steam effluent as a vacuum generator. etc., resulting in an increase in energy consumption. Furthermore, since the catalyst liquid is highly corrosive, it is preferable to keep the temperature inside the evaporator as low as possible when selecting materials for the evaporator. Therefore, the operating conditions for evaporating water from the catalyst are determined from both energy consumption and corrosive considerations, and the degree of vacuum in the evaporator is usually 50 to 400 mm.
Hg, preferably 50-200 mmHg. At this time, the temperature of the catalyst liquid in the evaporator is approximately 50 to 90°C. The evaporation of water from the catalyst in the present invention is carried out by a batch method,
Although any continuous method can be used, the continuous method is a preferred embodiment because of ease of operation and the ability to obtain a catalyst concentrate with a stable catalyst concentration. [Operations and Effects] According to the present invention, after the reaction, the catalyst consisting of the copper halide complex or the copper halide complex and the alkali metal halide present in the organic phase can be easily removed without impairing its activity or without loss of the catalyst. Can be implemented. In addition, after the reaction, the obtained extract can be separated from the organic phase and combined with the resulting aqueous phase to evaporate the water to obtain a catalyst concentrate, which can be used as is for the next reaction. can. In addition, the organic phase obtained by the catalyst extraction operation is
It contains only 10 ppm or less of catalyst in terms of Cu () ions and 1 ppm or less in terms of Li ions, and by directly reducing it, highly pure 2,3,5-trimethylhydroquinone, which is a precursor of vitamin E, can be obtained. [Example] Hereinafter, the present invention will be explained in more detail with reference to Examples and Comparative Examples. Note that the reaction rate and yield in Examples and Comparative Examples are expressed on a molar basis. Reference example 1 Copper halide complex Li is placed in the four-necked flask of 1.
[CuCl 3 ]・2H 2 O44.6g, lithium chloride 31.8g, water
99.2 g and 80 g of n-hexanol were added and stirred at 950 rpm. Catalyst concentration at this time (Li[CuCl 3 ]+
LiCl) was 39.2wt%. The inside of the reaction system was replaced with a gas having an oxygen concentration of 40% and heated to 50°C. Then
460 g of a 30% hexanol solution of TMP was quantitatively added dropwise over 4 hours. Consumed oxygen was successively supplied by an oxygen holder. After the reaction was completed, it was separated into an organic phase and an aqueous phase (catalyst phase). The obtained organic phase was washed with water and then analyzed by gas chromatography. The result is reference example 1
and shown in Table 1.
【表】
比較例 1
参考例1と同様の実施態様で反応を行つた後、
分液し、分離された水相を銅()イオンについ
ては原子吸光分析、塩素イオンについては硝酸銀
による沈澱滴定により分析したところ銅ハロゲノ
錯体Li〔CuCl3〕30.3g、塩化リチウム28.4gが存
在した。水相中の銅ハロゲノ錯体、塩化リチウム
の量は仕込み量に対し各々68.6%、89.3%であつ
た。又、この時の触媒濃度は40.5%であつた。
実施例 1
参考例1と同様の実施態様で反応を行つた後、
分液し、分液された有機相を600g/Hrの速度で
3個の撹拌槽、3個の沈降相を有する向流抽出装
置に流した。第1、第2、第3撹拌槽における有
機相の滞留時間をそれぞれ30分、15分、10分及び
各沈降槽における有機相と沈降相に関して滞留時
間を40分とした。一方、水を90g/Hrの速度で
第3槽から第1槽に向けて流した。
第1槽内のPHを1.5〜1.7、第2槽内のPHを2.0〜
2.5に保つために4%の塩酸水溶液をPHメーター
により制御しながら断続的に第1槽、第2槽に送
液した。
連続的に約8時間の抽出操作を行つたが、水不
溶性の銅化合物の析出は認められなかつた。
抽出操作が定常状態に達した後、任意時間の間
隔で抽出液および抽出装置出口の有機相をサンプ
リングし、抽出液及び有機相中のCu()イオン
をキレート滴定により、Liイオンを原子吸光分
析、Clイオンを硝酸銀溶液による沈澱滴定により
分析し触媒の単位時間当りの回収量をし調べた。
結果を第2表に示す。表中、有機相中の抽出槽供
給前後の触媒含量は有機相を希硝酸で抽出後、抽
出液中のCu()、Li、Clイオンについて分析し
求めたものである。
得られた触媒水溶液は乾固状態になるまで水を
蒸発し触媒を固体として回収した。[Table] Comparative Example 1 After carrying out the reaction in the same manner as in Reference Example 1,
The separated aqueous phase was analyzed for copper () ions by atomic absorption spectrometry and for chlorine ions by precipitation titration with silver nitrate, and it was found that 30.3 g of copper halide complex Li [CuCl 3 ] and 28.4 g of lithium chloride were present. . The amounts of copper halide complex and lithium chloride in the aqueous phase were 68.6% and 89.3%, respectively, of the charged amount. Further, the catalyst concentration at this time was 40.5%. Example 1 After carrying out a reaction in the same manner as in Reference Example 1,
The organic phase was separated, and the separated organic phase was passed through a countercurrent extraction device having three stirring tanks and three settling phases at a rate of 600 g/hr. The residence time of the organic phase in the first, second, and third stirring tanks was 30 minutes, 15 minutes, and 10 minutes, respectively, and the residence time of the organic phase and sedimentation phase in each settling tank was 40 minutes. On the other hand, water was flowed from the third tank to the first tank at a rate of 90 g/Hr. PH in the first tank is 1.5-1.7, PH in the second tank is 2.0-
In order to maintain the pH at 2.5, a 4% hydrochloric acid aqueous solution was intermittently sent to the first and second tanks while being controlled by a PH meter. Although the extraction operation was carried out continuously for about 8 hours, no precipitation of water-insoluble copper compounds was observed. After the extraction operation reaches a steady state, sample the extract liquid and the organic phase at the exit of the extraction device at arbitrary time intervals, and perform chelate titration to detect Cu () ions in the extract liquid and organic phase, and perform atomic absorption spectrometry for Li ions. The amount of catalyst recovered per unit time was determined by analyzing Cl ions by precipitation titration using a silver nitrate solution.
The results are shown in Table 2. In the table, the catalyst content in the organic phase before and after supply to the extraction tank was determined by extracting the organic phase with dilute nitric acid and then analyzing Cu(), Li, and Cl ions in the extract. Water was evaporated from the resulting catalyst aqueous solution until it became dry, and the catalyst was recovered as a solid.
【表】
比較例 2
実施例1において第1槽、第2槽に塩酸を供給
しないで抽出操作を行つた。
抽出操作開始後1時間で水不溶性の銅化合物の
析出のため各槽、各沈降槽からの液の抜き出しが
不可能になつた。
実施例 2〜3
実施例1において各抽出槽の滞留時間を次のよ
うにして抽出操作を行つた。その結果は第3表の
通りであつた。
得られた触媒水溶液は乾固状態になるまで水を
蒸発し触媒を固体として回収した。[Table] Comparative Example 2 In Example 1, the extraction operation was performed without supplying hydrochloric acid to the first tank and the second tank. One hour after the start of the extraction operation, it became impossible to extract the liquid from each tank and sedimentation tank due to the precipitation of water-insoluble copper compounds. Examples 2 to 3 In Example 1, the extraction operation was performed with the residence time in each extraction tank set as follows. The results were as shown in Table 3. Water was evaporated from the resulting catalyst aqueous solution until it became dry, and the catalyst was recovered as a solid.
【表】
実施例 4
参考例1と同様の実施態様で反応を行つた後、
相分離された水相(触媒相)と、実施例1と同様
にして得られた有機相の抽出液とを合わせ、これ
を減圧度100mmHgに保つた蒸発装置に270g/Hr
の速度で連続的に供給し、水を連続的に蒸発さ
せ、且つ濃縮触媒(回収触媒)を抜き出した。こ
の時の蒸発缶内の温度は73〜75℃であつた。
この回収触媒を用いた参考例1の半回分式の方
法で反応を行つた。得られた結果を第4表及び第
5表に示す。[Table] Example 4 After carrying out the reaction in the same manner as in Reference Example 1,
The phase-separated aqueous phase (catalyst phase) and the organic phase extract obtained in the same manner as in Example 1 were combined and transferred to an evaporator maintained at a reduced pressure of 100 mmHg at 270 g/Hr.
water was continuously evaporated, and the concentrated catalyst (recovered catalyst) was taken out. The temperature inside the evaporator at this time was 73 to 75°C. A reaction was carried out in the semi-batch method of Reference Example 1 using this recovered catalyst. The results obtained are shown in Tables 4 and 5.
【表】【table】
【表】
比較例 3
実施例1において第1槽、第2槽の触媒槽内の
PHを各々0.5〜1.0、1.0〜1.4に保ち抽出操作を行
い、ついで実施例4と同様にして触媒水溶液の濃
縮及び反応を行つた。その結果、実施例4よりも
反応速度が低下し、Cl−TMPが残りTMBQ収率
が低下した。得られた結果を第6表及び第7表に
示す。[Table] Comparative Example 3 In Example 1, the inside of the catalyst tanks of the first tank and the second tank
Extraction operations were carried out while keeping the pH at 0.5-1.0 and 1.0-1.4, respectively, and then the aqueous catalyst solution was concentrated and the reaction was carried out in the same manner as in Example 4. As a result, the reaction rate was lower than in Example 4, and Cl-TMP remained and the TMBQ yield decreased. The results obtained are shown in Tables 6 and 7.
【表】【table】
第1図は触媒回収の流れ図、第2図は向流多段
抽出装置を用いた抽出の流れ図を例示したもので
ある。第2図中、1,2,3はそれぞれ第1、第
2、第3撹拌槽を、4,5,6はそれぞれ第1、
第2、第3沈降槽を示す。
FIG. 1 is a flowchart of catalyst recovery, and FIG. 2 is a flowchart of extraction using a countercurrent multi-stage extraction device. In Figure 2, 1, 2, and 3 are the first, second, and third stirring tanks, respectively, and 4, 5, and 6 are the first and third stirring tanks, respectively.
The second and third settling tanks are shown.
Claims (1)
Mは周期律表においてIAで表されるアルカリ金
属またはアンモニウム、Cu()は二価の銅、X
はハロゲン、lは1〜3の整数、mは1または
2、nは3〜8の整数、pは1または2〕 で示される銅ハロゲノ錯体、又は該銅ハロゲノ錯
体とアルカリ金属ハロゲン化物からなる触媒を用
いて水及び炭素数5〜10の脂肪族アルコール中で
2,3,6−トリメチルフエノールを酸素又は酸
素含有ガスと接触させ2,3,5−トリメチルベ
ンゾキノンを製造する方法において、 反応後、分液された有機相より水を用いて抽出
装置内のPHを1.5〜2.5に保ちながら触媒を抽出
し、次いで抽出液内の水を蒸発させて触媒を回収
することを特徴とする触媒の回収方法。 2 向流多段撹拌槽を用い触媒を抽出する特許請
求の範囲第1項記載の方法。 3 触媒を抽出するために用いる水の量を反応後
分液された有機相に対して10〜30wt%とする特
許請求の範囲第1項記載の方法。 4 向流多段撹拌槽を2〜5段とする特許請求の
範囲第2項記載の方法。 5 向流多段撹拌槽の各槽の間に沈降槽をおく特
許請求の範囲第2項記載の方法。 6 向流多段撹拌槽における有機相の滞留時間を
10〜60分とする特許請求の範囲第2項記載の方
法。 7 撹拌槽におけるPHを1.5〜2.5に保つためにハ
ロゲン化水素酸水溶液を添加する特許請求の範囲
第2項記載の方法。 8 ハロゲン化水素酸水溶液として1〜10重量%
の塩酸を用いるを添加する特許請求の範囲第7項
記載の方法。 9 抽出液中の水を50〜200Torrの真空下、連続
的に蒸発させる特許請求の範囲第1項記載の方
法。[Claims] 1 General formula Ml[Cu()mXn]p (which may or may not contain water of crystallization) [in the formula,
M is an alkali metal or ammonium represented by IA in the periodic table, Cu () is divalent copper, X
is a halogen, l is an integer of 1 to 3, m is 1 or 2, n is an integer of 3 to 8, p is 1 or 2], or the copper halogeno complex and an alkali metal halide. In a method for producing 2,3,5-trimethylbenzoquinone by contacting 2,3,6-trimethylphenol with oxygen or an oxygen-containing gas in water and an aliphatic alcohol having 5 to 10 carbon atoms using a catalyst, after the reaction. , the catalyst is extracted from the separated organic phase using water while maintaining the pH in the extractor at 1.5 to 2.5, and then the water in the extract is evaporated to recover the catalyst. Collection method. 2. The method according to claim 1, wherein the catalyst is extracted using a countercurrent multistage stirring tank. 3. The method according to claim 1, wherein the amount of water used to extract the catalyst is 10 to 30 wt% based on the organic phase separated after the reaction. 4. The method according to claim 2, wherein the countercurrent multistage stirring tank has 2 to 5 stages. 5. The method according to claim 2, wherein a settling tank is provided between each tank of the countercurrent multistage stirring tank. 6 Residence time of organic phase in countercurrent multistage stirring tank
The method according to claim 2, wherein the heating time is 10 to 60 minutes. 7. The method according to claim 2, wherein a hydrohalic acid aqueous solution is added to maintain the pH in the stirring tank at 1.5 to 2.5. 8 1 to 10% by weight as an aqueous solution of hydrohalic acid
8. The method according to claim 7, wherein the method is performed using hydrochloric acid. 9. The method according to claim 1, wherein water in the extract is continuously evaporated under a vacuum of 50 to 200 Torr.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP59163403A JPS6140239A (en) | 1984-08-02 | 1984-08-02 | Method for recovering catalyst |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP59163403A JPS6140239A (en) | 1984-08-02 | 1984-08-02 | Method for recovering catalyst |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPS6140239A JPS6140239A (en) | 1986-02-26 |
| JPH0463869B2 true JPH0463869B2 (en) | 1992-10-13 |
Family
ID=15773228
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP59163403A Granted JPS6140239A (en) | 1984-08-02 | 1984-08-02 | Method for recovering catalyst |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPS6140239A (en) |
Families Citing this family (3)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JP6561049B2 (en) | 2013-07-02 | 2019-08-14 | ビーエーエスエフ ソシエタス・ヨーロピアBasf Se | Method for producing 2,3,5-trimethylbenzoquinone by oxidation of 2,3,6-trimethylphenol |
| JP2019034945A (en) * | 2013-07-02 | 2019-03-07 | ビーエーエスエフ ソシエタス・ヨーロピアBasf Se | Process for producing 2,3,5-trimethylbenzoquinone by oxidation of 2,3,6-trimethylphenol |
| CN109513461B (en) * | 2018-10-23 | 2021-12-28 | 南京工业大学 | Polymer-supported copper catalyst, preparation and application thereof |
-
1984
- 1984-08-02 JP JP59163403A patent/JPS6140239A/en active Granted
Also Published As
| Publication number | Publication date |
|---|---|
| JPS6140239A (en) | 1986-02-26 |
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