Deprecated: The each() function is deprecated. This message will be suppressed on further calls in /home/zhenxiangba/zhenxiangba.com/public_html/phproxy-improved-master/index.php on line 456
JPH0419980B2 - - Google Patents
[go: Go Back, main page]

JPH0419980B2 - - Google Patents

Info

Publication number
JPH0419980B2
JPH0419980B2 JP57123426A JP12342682A JPH0419980B2 JP H0419980 B2 JPH0419980 B2 JP H0419980B2 JP 57123426 A JP57123426 A JP 57123426A JP 12342682 A JP12342682 A JP 12342682A JP H0419980 B2 JPH0419980 B2 JP H0419980B2
Authority
JP
Japan
Prior art keywords
catalyst
mmol
reaction
phenol
phenols
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
JP57123426A
Other languages
Japanese (ja)
Other versions
JPS5913743A (en
Inventor
Takao Maki
Tetsuo Masuyama
Toshiharu Yokoyama
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.)
Mitsubishi Chemical Corp
Original Assignee
Mitsubishi Chemical Industries Ltd
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 Mitsubishi Chemical Industries Ltd filed Critical Mitsubishi Chemical Industries Ltd
Priority to JP57123426A priority Critical patent/JPS5913743A/en
Publication of JPS5913743A publication Critical patent/JPS5913743A/en
Publication of JPH0419980B2 publication Critical patent/JPH0419980B2/ja
Granted legal-status Critical Current

Links

Classifications

    • YGENERAL 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
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02PCLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
    • Y02P20/00Technologies relating to chemical industry
    • Y02P20/50Improvements relating to the production of bulk chemicals
    • Y02P20/52Improvements 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

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

本発明は、フエノール類製造用触媒の回収法に
係り、更に詳しくは、ベンゼンモノカルボン酸類
又はその塩、エステルあるいは無水物から、液相
にて酸化脱炭酸反応により、ベンゼンモノカルボ
ン酸フエノールエステル類を経てその加水分解生
成物であるフエノール類を製造する工程におい
て、使用された銅化合物、マンガン化合物及び希
土化合物よりなる触媒を燃焼により回収する方法
に関する。 ベンゼンモノカルボン酸類又はその塩、エステ
ルあるいは無水物を、液相にて銅化合物、マンガ
ン化合物及び希土類化合物より構成される触媒
(以下、本触媒という。)の存在下、分子状酸素含
有ガスと接触させることにより、フエノール類を
極めて高選択的に製造できることは、先に本発明
者等により特願昭56−132481号、同56−159716
号、同56−177582号等の各明細書で明らかにされ
ている。このように上記本触媒系は、高性能でか
つフエノール生成の選択率は高いものの、タール
成分及びその前駆体であるフエノキシ安息香酸類
やヒドロキシ安息香酸類等の高沸点副生物が少量
生成することは避けられず、反応終了後フエノー
ル類等の軽沸点成分をガス成分とともに適当な手
段で回収すると、反応生成物にはタール成分、高
沸点副生物及び触媒成分の混合物が残存する。こ
のタール成分は触媒性能を低下させるので除去す
る必要であるが、本触媒は反応生成物に溶解して
おり、しかも本触媒は高価なためタールと一緒に
廃棄することは経済的に不利であるから、工業的
見地からすれば本触媒はどうしてもタールと分離
して再使用する必要がある。 本発明者等は、かかる実情に鑑み、反応生成物
から触媒有効成分を回収する方法について鋭意検
討した結果、反応生成物から目的生成物のフエノ
ール類及び未反応原料等の有価物質を適当な手段
で分離した後、残存する触媒とタール等を含む物
質を燃焼することにより、触媒有効成分を再使用
に支障のない状態で回収できること、しかもその
際の触媒の構成成分としては、銅化合物、マンガ
ン化合物及び希土化合物を同時に含む場合に限り
かかる回収方法が有効であつて、上記本触媒で例
えば希土化合物を構成成分として欠く場合には、
驚くべきことに、再使用による触媒性能の劣化が
認められてかかる回収法の適用が困難であること
などを初めて見い出し、本発明に到達した。すな
わち、本発明の要旨は、ベンゼンモノカルボン酸
類又はその塩、エステルあるいは無水物から、液
相にて銅化合物、マンガン化合物及び希土化合物
より構成される触媒の存在下、酸化脱炭酸反応に
よりフエノール類を製造する工程において、フエ
ノール類を分離した後の反応生成物を燃焼するこ
とにより触媒成分を回収することを特徴とするフ
エノール類製造用触媒の回収法に存する。なお、
かかる要旨の本発明の触媒回収法は、酸化反応と
加水分解反応とを、同時に行う一段反応方法ある
いは別個に行う二段反応方法のいずれによるフエ
ノール類の製造法にも適用可能である。 本発明方法における燃焼方法は、特に限定され
るものでなく、一般の油等の液状あるいは固体の
可燃物により着火して空気とともに燃焼させる方
法であつて、燃焼後触媒有効成分を減少させるこ
となく回収できる装置を付帯しているものを用い
る方法であれば、どのような方法でもよい。例え
ば、リン酸の濃縮やロジウム法プロピレンオキソ
反応のロジウム回収法等に用いられる水中燃焼法
などは適用可能である。また、燃焼後触媒は酸化
物の形で回収されることが多いが、これを反応物
に混入すると、均一に溶解して再使用することが
できる。この場合、反応物中では、各触媒成分は
恐らくはカルボン酸塩となつて存在していると推
定される。 一方、本発明でいう反応生成物とは、ベンゼン
モノカルボン酸類等の原料から、液相にて銅化合
物、マンガン化合物及び希土化合物からなる触媒
の存在下、酸化脱炭酸反応により、ベンゼンモノ
カルボン酸フエノールエステル類を経てその加水
分解生成物であるフエノール類を製造する工程に
おける反応生成物から目的生成物のフエノール類
を分離回収した後の反応生成物であり、その一般
的組成は、原料のベンゼンモノカルボン酸70〜90
重量%、触媒金属成分2〜10重量%、タール1〜
5重量%、その他フエノール中間体のフエノール
エステル類等5〜15重量%である。フエノール類
分離後のかかる反応生成物をそのまま燃焼させる
ことは、反応原料及びフエノール中間体をも同時
に失うことになるので、以下の二つの方法と組合
せることが、より経済的で特に工業的見地から望
ましい。 (i) フエノール類を分離した後の反応生成物か
ら、さらにまず蒸留により原料であるベンゼン
モノカルボン酸類及びフエノール中間体である
フエノールエステル類を分離した後、残存する
タール及び触媒成分を燃焼して触媒を回収する
方法である。この場合、蒸留後における原料ベ
ンゼンモノカルボン酸類の残存濃度が低下し、
その結果触媒成分の各金属塩が金属として析出
することは好ましくないので、少なくとも上記
触媒成分の各金属が塩を形成し安定して存在す
るのに必要なアニオン濃度、すなわち銅、マン
ガン及び希土の各金属モル濃度に対し、少なく
ともそれぞれの金属イオン価に対応し得るよう
に2倍、3倍及び3倍以上のモル濃度のカルボ
ン酸アニオンが存在する量の原料ベンゼンモノ
カルボン酸類が残存するように調節する必要が
ある。 (ii) フエノール類分離後の反応生成物から、水抽
出等により大部分の触媒成分及び反応原料並び
にフエノール中間体を抜き出し、これを反応器
に再循環し、一方、水抽出等の後に一部残存す
る触媒と大部分残存するタールとを燃焼させて
回収した触媒成分は反応器に再循環する方法で
ある。 しかして、本発明の燃焼触媒回収法を上記(i)の
方法と組合せた一例及び上記(ii)の方法と組合せた
一例のそれぞれは、第1図及び第2図の各フエノ
ール製造工程図に組込んで示した通りである。 次に本発明を実施例により更に具体的に説明す
る。 実施例 1 容量300mlの邪魔板付(5mm×40mm,3枚)回
転撹拌式(径20mmφの半円形テフロン製撹拌板
付)四つ口丸底型ガラス反応器に安息香酸134.7
g(1103.2mmol)、塩基性炭酸銅(CuCO3・Cu
(OH)2・H2O)1.61g(6.4mmol)、酸化マンガ
ン(Mn O)1.82g(25.6mmol)及び工業用ジ
ジム(La2O356.3%,Nd2O333.0%,Pr6O118.8
%,Sm2O31.5%)4.17gを仕込み、これにガス
導入口及び蒸留管を接続し、マントル炉により反
応器を加熱した。反応温度235℃に到達後、加熱
された空気及び蒸気化された水をそれぞれ30/
hr(NTP)及び30g/hrの流量で反応器底部より
溶融安息香酸中に吹き込み、酸化脱炭酸反応を開
始した。撹拌板の回転数は1300rpmであつた。ガ
ス成分及びフエノールを含む軽沸点液成分は、反
応器に接続された蒸留管(内径30mm,高さ300mm
のヴイグニー管)で蒸留分離され、液成分は液ト
ラツプに捕集され、その間蒸留管は110〜130℃に
温度制御されていた。酸化脱炭酸反応は135分後
に停止し、反応器残液及び液トラツプに捕集され
た留出液を、各々1,4−ジオキサンで希釈溶解
して500mlとした。 留出液については、その1,4−ジオキサン希
釈液500mlから各10ml取出し、液体クロマトグラ
フイーにより、それぞれフエノール(以下、
PHLと略記する。)、安息香酸(以下、BAと略記
する。)及び安息香酸フエニル(以下、PHBAと
略記する。)を定量した。 また、反応器残液については、中沸点生成物の
定量及びタール量の測定を行つた。定量した中沸
点生成物は、サリチル酸(以下、BAと略記す
る。)、m−,及びp−ヒドロキシ安息香酸(以
下、HOBAと略記する。)、o−,m−,及びp
−フエノキシ安息香酸(以下、POBAと略記す
る。)、m−,及びp−ベンゾイルオキシ安息香酸
(以下、BOBAと略記する。)並びにジフエニル
エーテル(以下、DPEと略記する。)であつた。
なお、反応中間体と考られるo−ベンゾイルオキ
シ安息香酸は認められなかつた。これらの分析は
次のようにして行つた。即ち、上記した反応器残
液の1,4−ジオキサン希釈液500mlから10ml取
出し、1,4−ジオキサンを釜温110〜130℃で蒸
留により留去後、常温に戻した。これにジエチル
エーテル20ml及び2N塩酸20mlを加え、十分に振
動抽出操作を行つた後、触媒成分を含む水層を抜
き出し、エーテル層をジアゾメタン化法によりメ
チルエーテル化した後、ガスクロマトグラフイー
により定量した。また、タール量は、以下の方法
により求めた。即ち、上記した反応器残液の1,
4−ジオキサン希釈液から100ml取出し、1,4
−ジオキサンを釜温110〜130℃で蒸留により留去
後、常温に戻した。これにジエチルエーテル200
ml及び2N塩酸200mlを加え、十分に振動抽出操作
を行つた後、触媒成分を含む水層を抜き出し、エ
ーテル層に飽和炭酸水素ナトリウム水溶液100ml
を加え、十分に振動抽出操作を行い、安息香酸等
の酸性物質を抽出した。この操作をもう一度繰り
返した。その後エーテル層をろ過し、漏斗上に残
存したろ滓を十分にジエチルエーテルで洗浄し、
乾燥後、ろ滓の重量測定を行い、タール量とし
た。 以上の分析を行つた結果、留出液中には
PHL17.24g(183.2mmol)及びBA4.48g
(36.7mmol)が認められ、また反応器残液中には
PHL1.53g(16.3mmol)、BA92.63g
(758.6mmol)、PHBA10.85g(53.2mmol)、
SA0.12g(0.88mmol)、o−POBA0.65g
(3.0mmol)、(m+p)−BOBA0.71g
(2.8mmol)、及びタール量0.16g(PHL換算
1.6mmol)が認められた。転化率、選択率及びφ
バランス(ベンゼン環バランス)については後記
表−1に示す。 次に、上記した1,4−ジオキサンに希釈溶解
された反応器残液から、1,4−ジオキサン、原
料の安息香酸、フエノール中間体の安息香酸フエ
ノールエステル等を蒸留により留去させ、残存す
る固形物を内径30mmの石英ガラス管に充てんし、
500℃で3時間空気を適量流しながら焼成した。
焼成物は黒色の粉体であつた。これに先の分析で
失なわれた触媒量に相当する塩基性炭酸銅、酸化
マンガン及び工業用ジジムを加え、最初の実験と
同様にして酸化脱炭酸反応を行い、そして同様な
分析を行つた。結果を表−1に示す。更にこれら
の操作を2回繰り返した結果も同じく後記表−1
にまとめて比較表示する。 実施例 2 内径31mm、高さ210mmの四つ口分離型円筒状ガ
ラス反応器を使用し、工業用ジジムの代りに酸化
ランタン(La2O3)4.17g(12.8mmol)を使用
し、加熱空気量を15/hr(NTP)吹き込み、か
つ反応時間を6時間にした以外は、実施例1と同
様に反応、分析及び焼成処理を行つた。結果を後
記表−2に示す。 比較例 1 酸化ランタンを添加しない以外は、実施例2と
同様に行つた。この結果は、実施例2の結果との
比較のため、後記表−2にまとめて表示する。
The present invention relates to a method for recovering a catalyst for producing phenols, and more specifically, the present invention relates to a method for recovering a catalyst for producing phenols, and more particularly, a method for recovering benzene monocarboxylic acid phenol esters from benzene monocarboxylic acids or their salts, esters, or anhydrides through an oxidative decarboxylation reaction in the liquid phase. The present invention relates to a method for recovering, by combustion, a catalyst consisting of a copper compound, a manganese compound, and a rare earth compound used in the process of producing phenols, which are hydrolyzed products thereof. Benzene monocarboxylic acids or their salts, esters, or anhydrides are brought into contact with a molecular oxygen-containing gas in the presence of a catalyst composed of a copper compound, a manganese compound, and a rare earth compound (hereinafter referred to as the catalyst) in a liquid phase. The fact that phenols can be produced with extremely high selectivity by
No. 56-177582, etc. As described above, although this catalyst system has high performance and a high selectivity for phenol production, it avoids the production of small amounts of high-boiling point byproducts such as tar components and their precursors, such as phenoxybenzoic acids and hydroxybenzoic acids. If the light-boiling components such as phenols are recovered together with the gas components by appropriate means after the reaction is completed, a mixture of tar components, high-boiling by-products, and catalyst components remains in the reaction product. This tar component degrades catalyst performance and must be removed, but since the catalyst is dissolved in the reaction products and is expensive, it is economically disadvantageous to dispose of it together with the tar. Therefore, from an industrial standpoint, it is necessary to separate the catalyst from the tar and reuse it. In view of these circumstances, the inventors of the present invention have conducted intensive studies on methods for recovering catalytic active components from reaction products, and have discovered that valuable substances such as target phenols and unreacted raw materials can be recovered from reaction products by appropriate means. After separation, the remaining catalyst and substances containing tar can be burned to recover the active catalyst components in a state that does not pose a problem for reuse. This recovery method is effective only when the compound and the rare earth compound are contained at the same time, and when the present catalyst lacks the rare earth compound as a component, for example,
Surprisingly, it was discovered for the first time that deterioration of catalyst performance was observed due to reuse, making it difficult to apply such a recovery method, and the present invention was thus achieved. That is, the gist of the present invention is to produce phenol from benzene monocarboxylic acids or their salts, esters, or anhydrides through an oxidative decarboxylation reaction in the liquid phase in the presence of a catalyst composed of a copper compound, a manganese compound, and a rare earth compound. The present invention relates to a method for recovering a catalyst for producing phenols, which comprises recovering a catalyst component by burning a reaction product after separating phenols in a process for producing phenols. In addition,
The catalyst recovery method of the present invention having this gist can be applied to a method for producing phenols using either a one-stage reaction method in which an oxidation reaction and a hydrolysis reaction are performed simultaneously or a two-stage reaction method in which the oxidation reaction and the hydrolysis reaction are performed separately. The combustion method in the method of the present invention is not particularly limited, and is a method of igniting with a liquid or solid combustible material such as general oil and burning it with air, without reducing the catalytic active component after combustion. Any method that uses a device that can be recovered may be used. For example, an underwater combustion method used for concentrating phosphoric acid or recovering rhodium in the rhodium propylene oxo reaction can be applied. Further, the post-combustion catalyst is often recovered in the form of an oxide, but if this is mixed into the reactants, it can be uniformly dissolved and reused. In this case, it is estimated that each catalyst component probably exists in the form of a carboxylic acid salt in the reactant. On the other hand, the reaction product referred to in the present invention is benzene monocarboxylic acid produced by oxidative decarboxylation reaction from raw materials such as benzene monocarboxylic acids in the presence of a catalyst consisting of a copper compound, a manganese compound, and a rare earth compound in the liquid phase. It is a reaction product obtained by separating and recovering the target product phenols from the reaction product in the process of producing phenols, which are the hydrolysis products of acid phenol esters, and its general composition is based on the raw material. Benzene monocarboxylic acid 70~90
Weight%, catalyst metal component 2~10% by weight, tar 1~
5% by weight, and 5 to 15% by weight of other phenol intermediates such as phenol esters. Burning the reaction product after separating the phenols as it is will result in the simultaneous loss of the reaction raw material and the phenol intermediate, so it is more economical and especially from an industrial standpoint to combine it with the following two methods. desirable. (i) From the reaction product after separating the phenols, first, the benzene monocarboxylic acids that are raw materials and the phenol esters that are phenol intermediates are separated by distillation, and then the remaining tar and catalyst components are burned. This is a method of recovering the catalyst. In this case, the residual concentration of raw benzene monocarboxylic acids after distillation decreases,
As a result, it is undesirable for the metal salts of the catalyst components to precipitate as metals, so at least the anion concentration required for each of the metals of the catalyst components to form salts and stably exist, that is, copper, manganese, and rare earth. For each metal molar concentration, the raw benzene monocarboxylic acids remain in an amount such that carboxylic acid anions with a molar concentration of twice, three times, and three times or more are present so as to correspond to the respective metal ion valences at least. need to be adjusted. (ii) From the reaction product after separation of phenols, most of the catalyst components, reaction raw materials, and phenol intermediates are extracted by water extraction, etc., and recycled to the reactor; In this method, the remaining catalyst and most of the remaining tar are burned and the recovered catalyst components are recycled to the reactor. Therefore, an example in which the combustion catalyst recovery method of the present invention is combined with the method (i) above and an example in which it is combined with the method (ii) above are shown in the respective phenol production process diagrams in FIGS. 1 and 2. It is as shown incorporated. Next, the present invention will be explained in more detail with reference to Examples. Example 1 Benzoic acid 134.7 was placed in a four-neck round-bottom glass reactor with a rotating stirring type (with a semicircular Teflon stirring plate with a diameter of 20 mmφ) with baffle plates (5 mm x 40 mm, 3 pieces) with a capacity of 300 ml.
g (1103.2 mmol), basic copper carbonate ( CuCO3・Cu
(OH) 2 H 2 O) 1.61 g (6.4 mmol), manganese oxide (Mn O) 1.82 g (25.6 mmol) and industrial didymium (La 2 O 3 56.3%, Nd 2 O 3 33.0%, Pr 6 O 11 8.8
%, Sm 2 O 3 1.5%) was charged, a gas inlet and a distillation tube were connected to this, and the reactor was heated in a mantle furnace. After reaching the reaction temperature of 235°C, heated air and vaporized water were added at 30/30% each.
hr (NTP) and a flow rate of 30 g/hr was blown into the molten benzoic acid from the bottom of the reactor to start the oxidative decarboxylation reaction. The rotation speed of the stirring plate was 1300 rpm. Gas components and light boiling point liquid components including phenols are collected using a distillation tube (inner diameter 30 mm, height 300 mm) connected to the reactor.
The liquid components were collected in a liquid trap, during which time the temperature of the distillation tube was controlled at 110-130°C. The oxidative decarboxylation reaction was stopped after 135 minutes, and the reactor residual liquid and the distillate collected in the liquid trap were each diluted and dissolved with 1,4-dioxane to make 500 ml. Regarding the distillate, 10 ml of each was taken out from 500 ml of the 1,4-dioxane diluted solution, and phenol (hereinafter referred to as
Abbreviated as PHL. ), benzoic acid (hereinafter abbreviated as BA), and phenyl benzoate (hereinafter abbreviated as PHBA) were quantified. In addition, regarding the reactor residual liquid, the amount of intermediate boiling point products and the amount of tar were measured. The quantified medium-boiling point products were salicylic acid (hereinafter abbreviated as BA), m-, and p-hydroxybenzoic acid (hereinafter abbreviated as HOBA), o-, m-, and p-hydroxybenzoic acid (hereinafter abbreviated as HOBA).
-phenoxybenzoic acid (hereinafter abbreviated as POBA), m- and p-benzoyloxybenzoic acid (hereinafter abbreviated as BOBA), and diphenyl ether (hereinafter abbreviated as DPE).
Note that o-benzoyloxybenzoic acid, which is thought to be a reaction intermediate, was not observed. These analyzes were conducted as follows. That is, 10 ml of the 1,4-dioxane diluted solution of the above reactor residue was taken out, 1,4-dioxane was distilled off at a pot temperature of 110 to 130°C, and then the temperature was returned to room temperature. 20 ml of diethyl ether and 20 ml of 2N hydrochloric acid were added to this, and after thorough vibration extraction, the aqueous layer containing the catalyst component was extracted, and the ether layer was methyl etherified by the diazomethanation method, and then quantified by gas chromatography. . Moreover, the amount of tar was determined by the following method. That is, 1 of the above-mentioned reactor residual liquid,
Remove 100ml from the 4-dioxane diluted solution and add 1,4
-Dioxane was removed by distillation at a pot temperature of 110 to 130°C, and then the temperature was returned to room temperature. Add 200% diethyl ether to this
ml and 200 ml of 2N hydrochloric acid, and after thorough vibration extraction, extract the aqueous layer containing the catalyst component, and add 100 ml of a saturated aqueous sodium bicarbonate solution to the ether layer.
was added, and a vibration extraction operation was performed sufficiently to extract acidic substances such as benzoic acid. This operation was repeated once more. After that, the ether layer was filtered, and the filtrate remaining on the funnel was thoroughly washed with diethyl ether.
After drying, the weight of the filter dregs was measured to determine the amount of tar. As a result of the above analysis, it was found that the distillate contained
PHL17.24g (183.2mmol) and BA4.48g
(36.7 mmol) was observed in the reactor residual liquid.
PHL1.53g (16.3mmol), BA92.63g
(758.6mmol), PHBA10.85g (53.2mmol),
SA0.12g (0.88mmol), o-POBA0.65g
(3.0mmol), (m+p)-BOBA0.71g
(2.8 mmol), and tar amount 0.16 g (PHL equivalent)
1.6 mmol) was observed. Conversion rate, selectivity and φ
The balance (benzene ring balance) is shown in Table 1 below. Next, 1,4-dioxane, benzoic acid as a raw material, benzoic acid phenol ester as a phenol intermediate, etc. are distilled off from the reactor residual liquid diluted and dissolved in the above-mentioned 1,4-dioxane, and remain. Fill a quartz glass tube with an inner diameter of 30 mm with solid matter,
It was fired at 500°C for 3 hours with an appropriate amount of air flowing through it.
The fired product was a black powder. Basic copper carbonate, manganese oxide, and industrial didymium corresponding to the amount of catalyst lost in the previous analysis were added, oxidative decarboxylation was performed in the same manner as in the first experiment, and the same analysis was performed. . The results are shown in Table-1. Furthermore, the results of repeating these operations twice are also shown in Table 1 below.
Comparatively display the results. Example 2 A four-neck separated cylindrical glass reactor with an inner diameter of 31 mm and a height of 210 mm was used, 4.17 g (12.8 mmol) of lanthanum oxide (La 2 O 3 ) was used instead of industrial didymium, and heated air was used. The reaction, analysis, and calcination treatment were carried out in the same manner as in Example 1, except that the amount of injection was 15/hr (NTP) and the reaction time was 6 hours. The results are shown in Table 2 below. Comparative Example 1 The same procedure as in Example 2 was carried out except that lanthanum oxide was not added. The results are summarized in Table 2 below for comparison with the results of Example 2.

【表】【table】

【表】 上記表−1の結果から明らかなように、本発明
の方法により燃焼して回収した触媒成分の使用を
繰り返した2,3いずれの場合も、新しい触媒を
使用した1の場合に比べ、原料転化率、フエノー
ル及び全フエノールの各選択率がいずれも良好で
かつタール選択率が極めて低い点で全く遜色がな
い。このことは、本発明の燃焼触媒回収法によれ
ば、触媒を容易に繰り返して再使用することがで
き、工業上特に有利なことを明らかにするもので
ある。
[Table] As is clear from the results in Table 1 above, in both cases 2 and 3, in which the catalyst components recovered by combustion by the method of the present invention were repeatedly used, compared to case 1, in which a new catalyst was used. , raw material conversion rate, phenol and total phenol selectivity are all good, and the tar selectivity is extremely low. This makes it clear that the combustion catalyst recovery method of the present invention allows the catalyst to be easily and repeatedly reused, which is particularly advantageous industrially.

【表】 上記表−2の結果から明らかなように、銅−マ
ンガン−希土からなる本触媒系を用いる実施例2
においては、本発明の燃焼触媒回収法による触媒
の回収を繰り返して再使用した2,3,4の場合
は、新しい触媒を使用した1の場合に比べ、フエ
ノール及び全フエノールの各選択率がいずれも勝
るとも劣らない。しかるに、銅−マンガンからな
り希土を含まない触媒を用いる比較例1において
は、燃焼触媒回収法により触媒を回収して再使用
した2の場合は、新しい触媒を使用した1の場合
に比べ、特にフエノール選択率が著しく低下し、
このことはフエノール中間体である安息香酸フエ
ニルの加水分解速度が低下していることを意味し
好ましくない。 (注1) 安息香酸(BA)転化率(モル%):仕込み
BA(mmol)−回収BA(mmol)/仕込みBA(mmol)×100 (注2) フエノール(PHL)選択率(モル%):生
成PHL(mmol)/仕込みBA(mmol)−回収BA(mmol)×1
00 全フエノール(PHL)選択率(モル%): 生成PHL(mmol)+生成PHBA(mmol)/〔仕込みBA
(mmol)−回収BA(mmol)−生成PHBA(mmol)〕×100 PHBA:安息香酸フエニル 中沸点生成物選択率(モル%): 〔SA(mmol)+ΣHOBA(mmol)+2×ΣPOBA(mmol
)+2×ΣBOBA(mmol)/仕込みBA−回収BA(mmol)※
※+2×DPE(mmol)/ ×100 SA:サリチル酸 異性体の合計 HOBA:m−,及びヒドロキシ安息香酸 POBA:o−,m−,及びp−フエノキシ
安息香酸 BOBA:m−,及びp−ベンゾイルオキシ
安息香酸 DPE:ジフエニルエーテル タール選択率(PHL換算モル%):〔生成タール(mg
)/94.1〕/仕込みBA(mmol)−回収BA(mmol)×100 (注3) φバランス(モル%): 〔PHL(mmol)+2×PHBA(mmol)+SA(mmol)+
ΣHOBA(mmol)/仕込みBA(mmol)※ ※+2×ΣPOBA(mmol)+2×ΣBOBA(mmol)+(
生成タール(mg)/94.1)〕/ ×100
[Table] As is clear from the results in Table 2 above, Example 2 using this catalyst system consisting of copper-manganese-rare earth
In cases 2, 3, and 4, in which the catalyst was repeatedly recovered and reused by the combustion catalyst recovery method of the present invention, the selectivity of phenol and total phenol was lower than in case 1, in which a new catalyst was used. It's no better than that. However, in Comparative Example 1 using a catalyst made of copper-manganese and containing no rare earth, in Case 2, in which the catalyst was recovered and reused by the combustion catalyst recovery method, compared to Case 1, in which a new catalyst was used, In particular, the phenol selectivity decreased significantly,
This is undesirable because it means that the rate of hydrolysis of phenyl benzoate, which is a phenol intermediate, is reduced. (Note 1) Benzoic acid (BA) conversion rate (mol%): Preparation
BA (mmol) - Recovered BA (mmol) / Prepared BA (mmol) × 100 (Note 2) Phenol (PHL) selectivity (mol%): Produced PHL (mmol) / Prepared BA (mmol) - Recovered BA (mmol) ×1
00 Total phenol (PHL) selectivity (mol%): Produced PHL (mmol) + Produced PHBA (mmol) / [Preparation BA
(mmol) - recovered BA (mmol) - produced PHBA (mmol)] × 100 PHBA: phenyl benzoate Medium boiling point product selectivity (mol%): [SA (mmol) + ΣHOBA (mmol) + 2 × ΣPOBA (mmol)
) + 2 x ΣBOBA (mmol) / Preparation BA - Recovered BA (mmol) *
*+2×DPE (mmol)/×100 SA: Salicylic acid Total of isomers HOBA: m-, and hydroxybenzoic acid POBA: o-, m-, and p-phenoxybenzoic acid BOBA: m-, and p-benzoyloxy Benzoic acid DPE: Diphenyl ether Tar selectivity (PHL equivalent mol%): [Produced tar (mg
)/94.1]/Prepared BA (mmol) - Recovered BA (mmol) x 100 (Note 3) φ balance (mol%): [PHL (mmol) + 2 x PHBA (mmol) + SA (mmol) +
ΣHOBA (mmol) / Preparation BA (mmol)* *+2 x ΣPOBA (mmol) + 2 x ΣBOBA (mmol) + (
Generated tar (mg) / 94.1)] / ×100

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

第1図及び第2図は本発明の燃焼触媒回収法を
フエノールの製造工程に組込んだ各一例の工程図
である。
FIGS. 1 and 2 are process diagrams of one example of incorporating the combustion catalyst recovery method of the present invention into a phenol manufacturing process.

Claims (1)

【特許請求の範囲】[Claims] 1 ベンゼンモノカルボン酸類又はその塩、エス
テルあるいは無水物から、液相にて銅化合物、マ
ンガン化合物及び希土化合物より構成される触媒
の存在下、酸化脱炭酸反応によりフエノール類を
製造する工程において、フエノール類を分離した
後の反応生成物を燃焼することにより触媒成分を
回収することを特徴とするフエノール類製造用触
媒の回収法。
1. In the process of producing phenols from benzene monocarboxylic acids or their salts, esters, or anhydrides by oxidative decarboxylation reaction in the presence of a catalyst composed of a copper compound, a manganese compound, and a rare earth compound in a liquid phase, A method for recovering a catalyst for producing phenols, which comprises recovering catalyst components by burning a reaction product after separating phenols.
JP57123426A 1982-07-14 1982-07-14 Recovery of catalyst for preparation of phenol Granted JPS5913743A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP57123426A JPS5913743A (en) 1982-07-14 1982-07-14 Recovery of catalyst for preparation of phenol

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP57123426A JPS5913743A (en) 1982-07-14 1982-07-14 Recovery of catalyst for preparation of phenol

Publications (2)

Publication Number Publication Date
JPS5913743A JPS5913743A (en) 1984-01-24
JPH0419980B2 true JPH0419980B2 (en) 1992-03-31

Family

ID=14860263

Family Applications (1)

Application Number Title Priority Date Filing Date
JP57123426A Granted JPS5913743A (en) 1982-07-14 1982-07-14 Recovery of catalyst for preparation of phenol

Country Status (1)

Country Link
JP (1) JPS5913743A (en)

Families Citing this family (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US4829293A (en) * 1985-05-06 1989-05-09 Hewlett-Packard Company Method and apparatus for achieving variable and infinite persistence

Also Published As

Publication number Publication date
JPS5913743A (en) 1984-01-24

Similar Documents

Publication Publication Date Title
CN102199082B (en) Aromatic carboxylic acids and the recovery of oxidation catalyst
JP7141303B2 (en) Method for producing 5,5'-methylenedisalicylic acid
JP2002525346A (en) Methods for the isolation and removal of unwanted water from chemical reactions
JPH0419980B2 (en)
JPS6328659B2 (en)
JPH10504327A (en) Solid catalyst
US4405823A (en) Process for the production of phenols
JPS59175484A (en) Preparation of n-formylasparic anhydride
JPS6312460B2 (en)
US4002667A (en) Bis-(2-hydroxyethyl)-terephthalate
JPH0419981B2 (en)
JPS5929626A (en) Method for recovering active component in catalyst for preparing phenol
JPS642419B2 (en)
JPS6353175B2 (en)
US4760166A (en) Purification of diphenyl phthalates
JPH0210813B2 (en)
JPH0470289B2 (en)
JPH0699350B2 (en) Method for separating phenols and catechols
JPH11165079A (en) Acetic acid recovery method and catalyst recovery method in liquid phase air oxidation reaction
CN109369357B (en) A kind of method for preparing symmetrical diaryl ketone by catalytic oxidative carbonylation
JPS6245218B2 (en)
SU1047920A1 (en) Method of producing polyesters
JP2023152806A (en) Method for producing 4,4'-dihydroxybiphenyl-3,3'-dicarboxylic acid
JPH0210812B2 (en)
SU1293168A1 (en) Method of processing bottoms formed in isolating crotonaldehyde