JP2006045371A - Method for obtaining aromatic dihydroxy compound from waste aromatic polycarbonate - Google Patents
Method for obtaining aromatic dihydroxy compound from waste aromatic polycarbonate Download PDFInfo
- Publication number
- JP2006045371A JP2006045371A JP2004229046A JP2004229046A JP2006045371A JP 2006045371 A JP2006045371 A JP 2006045371A JP 2004229046 A JP2004229046 A JP 2004229046A JP 2004229046 A JP2004229046 A JP 2004229046A JP 2006045371 A JP2006045371 A JP 2006045371A
- Authority
- JP
- Japan
- Prior art keywords
- aromatic polycarbonate
- dihydroxy compound
- aromatic
- waste
- organic solvent
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Granted
Links
- 125000003118 aryl group Chemical group 0.000 title claims abstract description 150
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- 229920000515 polycarbonate Polymers 0.000 title claims abstract description 78
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- 238000000034 method Methods 0.000 title claims abstract description 76
- 239000002699 waste material Substances 0.000 title claims abstract description 44
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- 238000000354 decomposition reaction Methods 0.000 claims abstract description 42
- LFQSCWFLJHTTHZ-UHFFFAOYSA-N Ethanol Chemical compound CCO LFQSCWFLJHTTHZ-UHFFFAOYSA-N 0.000 claims abstract description 21
- 238000001914 filtration Methods 0.000 claims abstract description 21
- 229910000000 metal hydroxide Inorganic materials 0.000 claims abstract description 21
- 150000004692 metal hydroxides Chemical class 0.000 claims abstract description 21
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- 238000004519 manufacturing process Methods 0.000 claims description 20
- 238000006243 chemical reaction Methods 0.000 claims description 17
- 239000002994 raw material Substances 0.000 claims description 12
- HEDRZPFGACZZDS-UHFFFAOYSA-N Chloroform Chemical compound ClC(Cl)Cl HEDRZPFGACZZDS-UHFFFAOYSA-N 0.000 claims description 10
- 239000000706 filtrate Substances 0.000 claims description 10
- 125000004432 carbon atom Chemical group C* 0.000 claims description 6
- SCYULBFZEHDVBN-UHFFFAOYSA-N 1,1-Dichloroethane Chemical compound CC(Cl)Cl SCYULBFZEHDVBN-UHFFFAOYSA-N 0.000 claims description 5
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- HEMHJVSKTPXQMS-UHFFFAOYSA-M Sodium hydroxide Chemical compound [OH-].[Na+] HEMHJVSKTPXQMS-UHFFFAOYSA-M 0.000 description 15
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- UOCLXMDMGBRAIB-UHFFFAOYSA-N 1,1,1-trichloroethane Chemical compound CC(Cl)(Cl)Cl UOCLXMDMGBRAIB-UHFFFAOYSA-N 0.000 description 2
- 238000005160 1H NMR spectroscopy Methods 0.000 description 2
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- 239000003643 water by type Substances 0.000 description 1
- 239000008096 xylene 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
- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
- Y02W30/00—Technologies for solid waste management
- Y02W30/50—Reuse, recycling or recovery technologies
- Y02W30/62—Plastics recycling; Rubber recycling
Landscapes
- Separation, Recovery Or Treatment Of Waste Materials Containing Plastics (AREA)
Abstract
Description
本発明は、廃芳香族ポリカーボネートを低級アルコールでエステル交換反応により分解し、芳香族ジヒドロキシ化合物を得る方法に関する。また、分解して得られた芳香族ジヒドロキシ化合物をポリカーボネートの製造原料として使用する芳香族ポリカーボネートの製造方法に関する。 The present invention relates to a method for obtaining an aromatic dihydroxy compound by decomposing waste aromatic polycarbonate by a transesterification reaction with a lower alcohol. Moreover, it is related with the manufacturing method of the aromatic polycarbonate which uses the aromatic dihydroxy compound obtained by decomposition | disassembly as a manufacturing raw material of a polycarbonate.
芳香族ポリカーボネート(以下、PCと略すことがある)は、優れた機械的性質、電気的性質、耐熱性、耐寒性、透明性等を有しており、レンズ、コンパクトディスク等の光ディスク、建築材料、自動車部品、OA機器のシャーシー、カメラボディー等様々な用途に利用されている材料であり、その需要は年々増加している。PCの需要の増加に伴い、廃棄されるPC製品の多くは焼却若しくは地中に埋める等の方法で処理される。これは、PCの需要の増加から石油資源の枯渇を加速させるだけでなく、地球環境の悪化を促進する。そこで、廃棄されたプラスチックを再利用(リサイクル)することが重要になってきた。 Aromatic polycarbonate (hereinafter sometimes abbreviated as PC) has excellent mechanical properties, electrical properties, heat resistance, cold resistance, transparency, etc., optical disks such as lenses and compact disks, and building materials. These materials are used in various applications such as automobile parts, OA equipment chassis and camera bodies, and the demand for these materials is increasing year by year. Along with the increase in demand for PCs, many of the PC products to be discarded are processed by methods such as incineration or filling in the ground. This not only accelerates the depletion of petroleum resources due to the increasing demand for PC, but also promotes the deterioration of the global environment. Therefore, it has become important to reuse (recycle) discarded plastic.
廃プラスチックをリサイクルする方法としては、(1)廃プラスチックを熱エネルギーとして回収するサーマルリサイクル、(2)廃プラスチックを製品にある割合で混合し、加工して製品とするマテリアルリサイクル、(3)廃プラスチックを化学的に分解してプラスチックの原材料にまで戻して、プラスチック製造に再使用するケミカルリサイクルがある。これらのうち、サーマルリサイクルは、プラスチックを焼却して熱を取りだすので、二酸化炭素が生成し、本質的には地球環境を破壊し、資源を減少させていることになる。マテリアルリサイクルは、資源の消費や環境の負荷は一番少なく望ましいが、プラスチック自身の劣化は否めず、混合できる製品が限定され、混入できる割合が少なく、リサイクルできる量が限られるという問題がある。一方ケミカルリサイクルはプラスチックを原材料まで分解するので、新たなプラスチックの製造に利用され、元の製品を含め広範囲の用途に利用できるので、産業上有用なリサイクル方法といえる。 Methods for recycling waste plastic include (1) thermal recycling that recovers waste plastic as thermal energy, (2) material recycling that mixes and processes waste plastic in a certain proportion, and (3) waste. There is chemical recycling in which plastic is chemically decomposed and returned to plastic raw materials and reused for plastic manufacturing. Of these, thermal recycling incinerates plastic to extract heat, generating carbon dioxide, essentially destroying the global environment and reducing resources. Material recycling is preferable because it consumes the least amount of resources and reduces the environmental load. However, the plastic itself cannot be denied, and there are problems that the products that can be mixed are limited, the proportion that can be mixed is small, and the amount that can be recycled is limited. On the other hand, chemical recycling decomposes plastics into raw materials, so it can be used for the production of new plastics and can be used for a wide range of applications including the original product.
PCをケミカルリサイクルする方法として、例えば特許文献1には、アルカリ触媒の存在下、PCをフェノールで分解し、芳香族ジヒドロキシ化合物と炭酸ジアリールを回収する方法が示されている。また特許文献2にはトルエン、キシレン、ベンゼンまたはジオキサン溶剤中で、少量のアルカリを触媒として、エステル交換反応を行い、炭酸ジアルキルと芳香族ジヒドロキシ化合物を得る方法が示されている。特許文献3には、PCを塩化アルキル、エーテル類または芳香族炭化水素系溶媒等の溶媒と触媒としての3級アミンの存在下、低級アルコールとエステル交換させて芳香族ジヒドロキシ化合物と炭酸ジアルキルを得る方法が提案されている。 As a method for chemically recycling PC, for example, Patent Document 1 discloses a method in which PC is decomposed with phenol in the presence of an alkali catalyst to recover an aromatic dihydroxy compound and a diaryl carbonate. Patent Document 2 discloses a method for obtaining a dialkyl carbonate and an aromatic dihydroxy compound by performing a transesterification reaction in a toluene, xylene, benzene or dioxane solvent using a small amount of alkali as a catalyst. In Patent Document 3, PC is transesterified with a lower alcohol in the presence of a solvent such as an alkyl chloride, an ether or an aromatic hydrocarbon solvent and a tertiary amine as a catalyst to obtain an aromatic dihydroxy compound and a dialkyl carbonate. A method has been proposed.
しかしながら、特許文献1の方法は溶媒と分解生成物との分離回収工程が煩雑である。特許文献2の方法は反応終了後、水中に反応混合物を投入し、芳香族ジヒドロキシ化合物を晶出させるか、分解混合物の数倍の量の溶媒を投入して、芳香族ジヒドロキシ化合物を析出させ、水洗する方法であり、この方法は使用したアルコールおよび溶剤の回収が非常に煩雑である。また、使用した溶剤を固体芳香族ジヒドロキシ化合物から除去するのが困難である。特許文献3の方法は、触媒としての3級アミンが、有機溶媒より多量用いられており、エバポレータなどで減圧除去を試みても、3級アミン、炭酸ジアルキルおよび芳香族ジヒドロキシ化合物をそれぞれ分離するのが非常に困難である。さらに、得られた芳香族ジヒドロキシ化合物中に末端停止剤が含有しており、末端停止剤の分離も必要である。実際、ポリカーボネートを製造する際、反応初期段階に末端停止剤が混入していると分子量調節が困難になるという不都合がある。 However, in the method of Patent Document 1, the separation and recovery step of the solvent and the decomposition product is complicated. In the method of Patent Document 2, after completion of the reaction, the reaction mixture is introduced into water to crystallize the aromatic dihydroxy compound, or a solvent several times the amount of the decomposition mixture is introduced to precipitate the aromatic dihydroxy compound, This is a method of washing with water, and in this method, the recovery of the used alcohol and solvent is very complicated. It is also difficult to remove the solvent used from the solid aromatic dihydroxy compound. In the method of Patent Document 3, a tertiary amine as a catalyst is used in a larger amount than an organic solvent, and even if an attempt is made to remove under reduced pressure with an evaporator or the like, the tertiary amine, dialkyl carbonate and aromatic dihydroxy compound are separated. Is very difficult. Furthermore, a terminal terminator is contained in the obtained aromatic dihydroxy compound, and it is necessary to separate the terminal terminator. In fact, when manufacturing polycarbonate, there is an inconvenience that it is difficult to adjust the molecular weight if a terminal terminator is mixed in the initial stage of the reaction.
本発明の目的は、廃芳香族ポリカーボネート(例えば不要となったCD、CD−ROM、DVD等の芳香族ポリカーボネート製品)を安価で、分解時間が短く、大量に処理し、ポリカーボネート製造の原材料等に有用な高純度の芳香族ジヒドロキシ化合物を得る方法を提供することである。 It is an object of the present invention to process waste aromatic polycarbonate (for example, aromatic polycarbonate products such as CDs, CD-ROMs, and DVDs that are no longer needed) at low cost, with a short decomposition time, and in a large amount to be processed as a raw material for producing polycarbonate. It is to provide a method for obtaining useful high purity aromatic dihydroxy compounds.
本発明の他の目的は、得られた芳香族ジヒドロキシ化合物を用いてCD等に使用できる高品質の芳香族ポリカーボネートを製造する方法を提供することである。 Another object of the present invention is to provide a method for producing a high-quality aromatic polycarbonate that can be used for CD or the like using the obtained aromatic dihydroxy compound.
本発明のさらに他の目的は、溶融重合法による芳香族ポリカーボネートの製造や他産業用に有用な炭酸ジアルキルを得る方法を提供することである。 Still another object of the present invention is to provide a process for obtaining dialkyl carbonates useful for the production of aromatic polycarbonates by melt polymerization and for other industries.
本発明者らは、これらの問題を解決するために鋭意検討した結果、廃芳香族ポリカーボネートを有機溶媒に溶解し、分解触媒として金属水酸化物を使用し、アルコールでエステル交換反応により分解し、芳香族ジヒドロキシ化合物を得る方法において、廃芳香族ポリカーボネートの有機溶媒溶液中の不溶異物が多いと、ポリカーボネートの分解反応時に副反応が起こるためか、得られた芳香族ジヒドロキシ化合物の純度を低下せしめるとともに、この低純度の芳香族ジヒドロキシ化合物をポリカーボネート製造の原料として用いた際、得られる芳香族ポリカーボネート中の異物量が市販の芳香族ジヒドロキシ化合物を用いた場合よりも増えることが判り、その対処法を種々検討した結果、前記廃芳香族ポリカーボネートの有機溶媒溶液をろ過してそのろ液を使用することにより、上記目的が達成されることを見出し本発明に至った。 As a result of intensive studies to solve these problems, the present inventors have dissolved waste aromatic polycarbonate in an organic solvent, used a metal hydroxide as a decomposition catalyst, decomposed by an ester exchange reaction with alcohol, In the method of obtaining the aromatic dihydroxy compound, if there are many insoluble foreign matters in the organic solvent solution of the waste aromatic polycarbonate, a side reaction may occur during the decomposition reaction of the polycarbonate, or the purity of the obtained aromatic dihydroxy compound is lowered. When this low-purity aromatic dihydroxy compound is used as a raw material for polycarbonate production, it can be seen that the amount of foreign matter in the resulting aromatic polycarbonate is greater than when a commercially available aromatic dihydroxy compound is used. As a result of various studies, the organic solvent solution of the waste aromatic polycarbonate was filtered. Its Using the filtrate, leading to the present invention found that the above object can be achieved Te.
すなわち、本発明によれば、
1.廃芳香族ポリカーボネートを有機溶媒に溶解し、この廃芳香族ポリカーボネートの有機溶媒溶液をろ過し、そのろ液中の芳香族ポリカーボネートを炭素数1〜4のアルコールおよび金属水酸化物の存在下、エステル交換反応により分解反応させることを特徴とする廃芳香族ポリカーボネートから芳香族ジヒドロキシ化合物を得る方法。
That is, according to the present invention,
1. Dissolving the waste aromatic polycarbonate in an organic solvent, filtering the organic solvent solution of the waste aromatic polycarbonate, and esterifying the aromatic polycarbonate in the filtrate in the presence of an alcohol having 1 to 4 carbon atoms and a metal hydroxide. A method for obtaining an aromatic dihydroxy compound from waste aromatic polycarbonate, characterized by causing a decomposition reaction by an exchange reaction.
2.有機溶媒は、ハロゲン化炭化水素化合物である前項1記載の廃芳香族ポリカーボネートから芳香族ジヒドロキシ化合物を得る方法。 2. 2. The method for obtaining an aromatic dihydroxy compound from the waste aromatic polycarbonate according to item 1, wherein the organic solvent is a halogenated hydrocarbon compound.
3.有機溶媒は、ジクロロメタン、ジクロロエタンまたはクロロホルムである前項1記載の廃芳香族ポリカーボネートから芳香族ジヒドロキシ化合物を得る方法。 3. The method for obtaining an aromatic dihydroxy compound from the waste aromatic polycarbonate according to item 1, wherein the organic solvent is dichloromethane, dichloroethane or chloroform.
4.廃芳香族ポリカーボネートの有機溶媒溶液を孔径1〜10μmのフィルターでろ過する前項1記載の廃芳香族ポリカーボネートから芳香族ジヒドロキシ化合物を得る方法。 4). A method for obtaining an aromatic dihydroxy compound from waste aromatic polycarbonate according to item 1 above, wherein an organic solvent solution of waste aromatic polycarbonate is filtered with a filter having a pore size of 1 to 10 μm.
5.廃芳香族ポリカーボネートの有機溶媒溶液を孔径20μm以上のフィルターでろ過した後、孔径1〜10μmのフィルターでろ過する前項1記載の廃芳香族ポリカーボネートから芳香族ジヒドロキシ化合物を得る方法。 5. A method for obtaining an aromatic dihydroxy compound from waste aromatic polycarbonate according to item 1 above, wherein an organic solvent solution of waste aromatic polycarbonate is filtered with a filter having a pore size of 20 μm or more and then filtered with a filter having a pore size of 1 to 10 μm.
6.前項1記載の方法で得られた芳香族ジヒドロキシ化合物を芳香族ポリカーボネートの製造原料として用いる芳香族ポリカーボネートの製造方法。
が提供される。
6). A method for producing an aromatic polycarbonate, wherein the aromatic dihydroxy compound obtained by the method according to item 1 is used as a raw material for producing an aromatic polycarbonate.
Is provided.
以下、本発明を詳細に説明する。
本発明において、使用される廃芳香族ポリカーボネートは、界面重合法や溶融重合法等公知の方法で製造されたものでよく、分子量は粘度平均分子量で1000〜100000のものが好ましい。廃芳香族ポリカーボネートの形状はパウダー、ペレット、シート、フィルム、成形品等特に限定されない。例えば、CD、CD−R、DVD等の光ディスクにおいて、廃棄されたものや成形不良のものなど不要になった廃光ディスクをそのままあるいは印刷膜や金属膜を剥離し除去したものを分解に使用することもできる。また、分解に用いられる廃芳香族ポリカーボネートとして、ポリカーボネート製造途中に目標とする分子量に到達せず、パウダーあるいはペレット化されなかったポリカーボネートの溶液から溶媒を除去し、乾燥した固形物でもよい。ここで、ポリカーボネート樹脂の粘度平均分子量(M)は塩化メチレン100mlにポリカーボネート樹脂0.7gを20℃で溶解した溶液から求めた比粘度(ηsp)を次式に挿入して求めたものである。
ηsp/c=[η]+0.45×[η]2c(但し[η]は極限粘度)
[η]=1.23×10−4M0.83
c=0.7
Hereinafter, the present invention will be described in detail.
In the present invention, the waste aromatic polycarbonate to be used may be one produced by a known method such as an interfacial polymerization method or a melt polymerization method, and the molecular weight is preferably a viscosity average molecular weight of 1000 to 100,000. The shape of the waste aromatic polycarbonate is not particularly limited, such as powder, pellets, sheets, films, and molded products. For example, optical discs such as CDs, CD-Rs, DVDs, etc., which are no longer used, such as discarded ones or defective ones, are used as they are, or ones that have been removed by removing the printed film or metal film are used for disassembly. You can also. Further, the waste aromatic polycarbonate used for decomposition may be a solid obtained by removing the solvent from the solution of the polycarbonate that has not reached the target molecular weight during the production of the polycarbonate, and has not been pelletized or pelletized. Here, the viscosity average molecular weight (M) of the polycarbonate resin is obtained by inserting the specific viscosity (η sp ) obtained from a solution obtained by dissolving 0.7 g of the polycarbonate resin in 100 ml of methylene chloride at 20 ° C. into the following equation. .
η sp /c=[η]+0.45×[η] 2 c (where [η] is the intrinsic viscosity)
[Η] = 1.23 × 10 −4 M 0.83
c = 0.7
該ポリカーボネートは、ハイドロキノン、レゾルシノール、4,4′−ジヒドロキシジフェニル、1,4−ジヒドロキシナフタレン、ビス(4−ヒドロキシフェニル)メタン、ビス{(4−ヒドロキシ−3,5−ジメチル)フェニル}メタン、1,1−ビス(4−ヒドロキシフェニル)エタン、1,1−ビス(4−ヒドロキシフェニル)−1−フェニルエタン、2,2−ビス(4−ヒドロキシフェニル)プロパン(通称ビスフェノールA)、2,2−ビス{(4−ヒドロキシ−3−メチル)フェニル}プロパン、2,2−ビス{(4−ヒドロキシ−3,5−ジメチル)フェニル}プロパン、2,2−ビス{(3,5−ジブロモ−4−ヒドロキシ)フェニル}プロパン、2,2−ビス{(3−イソプロピル−4−ヒドロキシ)フェニル}プロパン、2,2−ビス{(4−ヒドロキシ−3−フェニル)フェニル}プロパン、2,2−ビス(4−ヒドロキシフェニル)ブタン、2,2−ビス(4−ヒドロキシフェニル)−3−メチルブタン、2,2−ビス(4−ヒドロキシフェニル)−3,3−ジメチルブタン、2,4−ビス(4−ヒドロキシフェニル)−2−メチルブタン、2,2−ビス(4−ヒドロキシフェニル)ペンタン、2,2−ビス(4−ヒドロキシフェニル)−4−メチルペンタン、1,1−ビス(4−ヒドロキシフェニル)シクロヘキサン、1,1−ビス(4−ヒドロキシフェニル)−4−イソプロピルシクロヘキサン、1,1−ビス(4−ヒドロキシフェニル)−3,3,5−トリメチルシクロヘキサン、9,9−ビス(4−ヒドロキシフェニル)フルオレン、9,9−ビス{(4−ヒドロキシ−3−メチル)フェニル}フルオレン、α,α′−ビス(4−ヒドロキシフェニル)−o−ジイソプロピルベンゼン、α,α′−ビス(4−ヒドロキシフェニル)−m−ジイソプロピルベンゼン、α,α′−ビス(4−ヒドロキシフェニル)−p−ジイソプロピルベンゼン、1,3−ビス(4−ヒドロキシフェニル)−5,7−ジメチルアダマンタン、4,4′−ジヒドロキシジフェニルスルホン、4,4′−ジヒドロキシジフェニルスルホキシド、4,4′−ジヒドロキシジフェニルスルフィド、4,4′−ジヒドロキシジフェニルケトン、4,4′−ジヒドロキシジフェニルエーテルおよび4,4′−ジヒドロキシジフェニルエステル等のジヒドロキシ化合物の単独または2種以上の混合物から製造されたものである。 The polycarbonate includes hydroquinone, resorcinol, 4,4′-dihydroxydiphenyl, 1,4-dihydroxynaphthalene, bis (4-hydroxyphenyl) methane, bis {(4-hydroxy-3,5-dimethyl) phenyl} methane, , 1-bis (4-hydroxyphenyl) ethane, 1,1-bis (4-hydroxyphenyl) -1-phenylethane, 2,2-bis (4-hydroxyphenyl) propane (commonly called bisphenol A), 2,2 -Bis {(4-hydroxy-3-methyl) phenyl} propane, 2,2-bis {(4-hydroxy-3,5-dimethyl) phenyl} propane, 2,2-bis {(3,5-dibromo- 4-hydroxy) phenyl} propane, 2,2-bis {(3-isopropyl-4-hydroxy) phenyl} propa 2,2-bis {(4-hydroxy-3-phenyl) phenyl} propane, 2,2-bis (4-hydroxyphenyl) butane, 2,2-bis (4-hydroxyphenyl) -3-methylbutane, , 2-bis (4-hydroxyphenyl) -3,3-dimethylbutane, 2,4-bis (4-hydroxyphenyl) -2-methylbutane, 2,2-bis (4-hydroxyphenyl) pentane, 2,2 -Bis (4-hydroxyphenyl) -4-methylpentane, 1,1-bis (4-hydroxyphenyl) cyclohexane, 1,1-bis (4-hydroxyphenyl) -4-isopropylcyclohexane, 1,1-bis ( 4-hydroxyphenyl) -3,3,5-trimethylcyclohexane, 9,9-bis (4-hydroxyphenyl) fluorene, 9,9- {(4-hydroxy-3-methyl) phenyl} fluorene, α, α'-bis (4-hydroxyphenyl) -o-diisopropylbenzene, α, α'-bis (4-hydroxyphenyl) -m-diisopropylbenzene , Α, α'-bis (4-hydroxyphenyl) -p-diisopropylbenzene, 1,3-bis (4-hydroxyphenyl) -5,7-dimethyladamantane, 4,4'-dihydroxydiphenylsulfone, 4,4 Single or two or more of dihydroxy compounds such as' -dihydroxydiphenyl sulfoxide, 4,4'-dihydroxydiphenyl sulfide, 4,4'-dihydroxydiphenyl ketone, 4,4'-dihydroxydiphenyl ether and 4,4'-dihydroxydiphenyl ester Made from a mixture of
本発明において、まず、廃芳香族ポリカーボネート樹脂を有機溶媒に溶解し、この廃芳香族ポリカーボネートの有機溶媒溶液をろ過する。 In the present invention, first, the waste aromatic polycarbonate resin is dissolved in an organic solvent, and the organic solvent solution of the waste aromatic polycarbonate is filtered.
前記有機溶媒としては25℃における芳香族ポリカーボネート樹脂の溶解度が50g/L以上である溶媒が好ましく、具体的にはジクロロメタン、クロロホルム、ジクロロエタン、トリクロロエタン、テトラクロロエタン、ジクロロエチレン等のハロゲン化炭化水素化合物溶媒が好ましく、ジクロロメタン、ジクロロエタンまたはクロロホルムがより好ましく、ジクロロメタン(塩化メチレン)が特に好ましく用いられる。これらの溶媒は芳香族ポリカーボネート樹脂の良溶媒で、芳香族ポリカーボネート樹脂の製造工程に反応溶媒として用いられており、分解して得られた芳香族ジヒドロキシ化合物にこれらの有機溶媒が残留していても、芳香族ポリカーボネート樹脂の製造に悪影響を及ぼさない利点がある。 As the organic solvent, a solvent having an aromatic polycarbonate resin solubility at 25 ° C. of 50 g / L or more is preferable. Specifically, halogenated hydrocarbon compound solvents such as dichloromethane, chloroform, dichloroethane, trichloroethane, tetrachloroethane, and dichloroethylene Dichloromethane, dichloroethane or chloroform is more preferable, and dichloromethane (methylene chloride) is particularly preferably used. These solvents are good solvents for aromatic polycarbonate resins and are used as reaction solvents in the production process of aromatic polycarbonate resins. Even if these organic solvents remain in the aromatic dihydroxy compounds obtained by decomposition, these solvents are used. There is an advantage that does not adversely affect the production of the aromatic polycarbonate resin.
有機溶媒の使用量は、廃芳香族ポリカーボネート樹脂100重量部に対し400重量部〜1000重量部の範囲が好ましい。有機溶媒の使用量が400重量部より少ないと芳香族ポリカーボネート樹脂が充分に溶解せず不溶分が増え芳香族ジヒドロキシ化合物の収量が低下することがあり、1000重量部より多いと分解反応速度が低下し分解反応時間が長くなり、また溶媒の回収コストが高くなることがある。なお、光ディスク等の成形品はあらかじめ0.1〜2cm程度の大きさに粉砕し、この粉砕物を溶解すると溶解時間が短縮されるため好ましい。 The amount of the organic solvent used is preferably in the range of 400 to 1000 parts by weight with respect to 100 parts by weight of the waste aromatic polycarbonate resin. If the amount of the organic solvent used is less than 400 parts by weight, the aromatic polycarbonate resin may not be sufficiently dissolved to increase the insoluble content, and the yield of the aromatic dihydroxy compound may decrease. If the amount exceeds 1000 parts by weight, the decomposition reaction rate decreases. However, the decomposition reaction time may be increased, and the solvent recovery cost may increase. In addition, it is preferable that a molded product such as an optical disk is pulverized to a size of about 0.1 to 2 cm in advance and the pulverized material is dissolved, because the dissolution time is shortened.
廃芳香族ポリカーボネートの有機溶媒溶液をろ過する方法としてはろ過器、遠心分離機等を使用する方法が挙げられる。 Examples of the method for filtering the organic solvent solution of the waste aromatic polycarbonate include a method using a filter, a centrifuge, and the like.
ろ過器は、好ましくは孔径1〜100μm、より好ましくは1〜50μm、さらに好ましくは1〜20μm、特に好ましくは1〜10μmのフィルターを備えている。有機溶媒溶液を貯槽したタンクから分解反応を行うタンクにポンプを使用して圧送するラインにろ過器を設置することが工業的に好ましい。この範囲の孔径を有するフィルターを使用することによりろ過時間が短く、またろ過されるべき印刷膜、金属膜、UV硬化膜、添加剤、充填剤等の異物がろ液と共に流出し難くなり好ましい。フィルターの材質はPET、ナイロン、セルロースなどの樹脂製、もしくはセラミック、ステンレスなどの金属製のものが好ましく用いられる。
また、ろ過時の差圧は好ましくは0.01〜0.5MPa、特に好ましくは0.1〜0.4MPaである。
The filter preferably includes a filter having a pore size of 1 to 100 μm, more preferably 1 to 50 μm, still more preferably 1 to 20 μm, and particularly preferably 1 to 10 μm. It is industrially preferable to install a filter in a line that uses a pump to pump a tank that performs a decomposition reaction from a tank that stores an organic solvent solution. Use of a filter having a pore size in this range is preferable because the filtration time is short, and foreign matters such as a printed film, a metal film, a UV cured film, an additive, and a filler to be filtered hardly flow out together with the filtrate. The filter material is preferably made of a resin such as PET, nylon or cellulose, or a metal such as ceramic or stainless steel.
Moreover, the differential pressure during filtration is preferably 0.01 to 0.5 MPa, particularly preferably 0.1 to 0.4 MPa.
また、遠心分離機は、その金属製脱水部(バスケット部)の孔径は1〜50mmが好ましく、5〜20mmが特に好ましい。また金属製脱水部に取り付けるろ過フィルターの材質は綿やPET、ナイロン製などの樹脂製が好ましく、ろ過フィルターの孔径が好ましくは5〜100μmである。遠心分離機を用いて好ましくは遠心力100〜1000G、より好ましくは遠心力200〜700Gの条件によりろ過する。 Moreover, 1-50 mm is preferable and, as for the hole diameter of the metal spin-drying | dehydration part (basket part), 5-20 mm is especially preferable. The material of the filtration filter attached to the metal dehydration part is preferably made of a resin such as cotton, PET, or nylon, and the pore size of the filtration filter is preferably 5 to 100 μm. Filtration is preferably performed using a centrifuge under conditions of a centrifugal force of 100 to 1000 G, more preferably a centrifugal force of 200 to 700 G.
廃芳香族ポリカーボネートの有機溶媒溶液は、前述の方法でろ過されるが、最終的には孔径1〜10μm、好ましくは1〜5μmのフィルターでろ過することが望ましい。また、孔径20μm以上、好ましくは20〜100μmのフィルターでろ過した後に孔径1〜10μm、好ましくは1〜5μmのフィルターでろ過する方法が望ましい。また、ろ過した後の10μm以上の不溶異物量はポリカーボネート樹脂100重量部に対して0.02重量部以下が好ましく、0.01重量部以下が特に好ましい。 The organic solvent solution of waste aromatic polycarbonate is filtered by the above-described method, but it is finally desirable to filter with a filter having a pore diameter of 1 to 10 μm, preferably 1 to 5 μm. Further, a method of filtering with a filter having a pore size of 1 to 10 μm, preferably 1 to 5 μm after filtering with a filter having a pore size of 20 μm or more, preferably 20 to 100 μm is desirable. Further, the amount of insoluble foreign matter of 10 μm or more after filtration is preferably 0.02 parts by weight or less, particularly preferably 0.01 parts by weight or less, relative to 100 parts by weight of the polycarbonate resin.
ろ過により廃芳香族ポリカーボネート樹脂中に含まれる異物が除去される。特に廃光ディスクを使用する際は、光ディスクの表面に印刷膜、金属膜、UV硬化膜等が施されており、これらの異物を除去することが重要である。これらの異物が存在すると芳香族ポリカーボネート樹脂の分解反応において副反応が起こるためか得られる芳香族ジヒドロキシ化合物の純度が低下し、さらに得られた芳香族ジヒドロキシ化合物を芳香族ポリカーボネート樹脂の製造工程に使用すると得られる芳香族ポリカーボネート樹脂は色相に劣り熱安定性が低下し、芳香族ポリカーボネート樹脂中の異物量も多くなり、微小異物を嫌う光ディスク用の基板等の用途に使用できないこととなる。 Foreign matter contained in the waste aromatic polycarbonate resin is removed by filtration. In particular, when a waste optical disk is used, a printed film, a metal film, a UV cured film, and the like are provided on the surface of the optical disk, and it is important to remove these foreign substances. If these foreign substances are present, a side reaction occurs in the decomposition reaction of the aromatic polycarbonate resin, resulting in a decrease in the purity of the aromatic dihydroxy compound, and the resulting aromatic dihydroxy compound is used in the production process of the aromatic polycarbonate resin. The resulting aromatic polycarbonate resin is inferior in hue and thermal stability is reduced, and the amount of foreign matter in the aromatic polycarbonate resin is increased, so that it cannot be used for applications such as optical disk substrates that dislike fine foreign matter.
次いで、廃芳香族ポリカーボネートの有機溶媒溶液をろ過したろ液は、そのろ液中の芳香族ポリカーボネートを炭素数1〜4のアルコールおよび金属水酸化物の存在下、エステル交換反応により分解反応(解重合反応)させる。金属水酸化物を触媒として使用すると分解反応が低温で進み易く好ましい。 Next, the filtrate obtained by filtering the organic solvent solution of the waste aromatic polycarbonate is subjected to a decomposition reaction (dissolution) of the aromatic polycarbonate in the filtrate by transesterification in the presence of an alcohol having 1 to 4 carbon atoms and a metal hydroxide. Polymerization reaction). Use of a metal hydroxide as a catalyst is preferable because the decomposition reaction easily proceeds at a low temperature.
芳香族ポリカーボネートの分解に使用される炭素数1〜4のアルコールとしては、メタノール、エタノール、1−プロパノール、2−プロパノール(イソプロピルアルコール)、1−ブタノール、2−ブタノール、2−メチル−1−プロパノール(イソブチルアルコール)、1,1−ジメチル−1−エタノール(t−ブチルアルコール)が挙げられる。特にメタノールが好ましい。炭素数5以上のアルコールでは、分解反応が遅く、精製、分離工程において、分離が難しくなるので好ましくない。 Examples of the alcohol having 1 to 4 carbon atoms used for the decomposition of the aromatic polycarbonate include methanol, ethanol, 1-propanol, 2-propanol (isopropyl alcohol), 1-butanol, 2-butanol, and 2-methyl-1-propanol. (Isobutyl alcohol) and 1,1-dimethyl-1-ethanol (t-butyl alcohol). Methanol is particularly preferable. Alcohols having 5 or more carbon atoms are not preferable because the decomposition reaction is slow and separation is difficult in the purification and separation steps.
アルコールの使用量は、芳香族ポリカーボネートのカーボネート結合1モルに対して、好ましくは2.4〜7モルであり、さらに好ましくは3〜7モルである。モル比が7モルより多いと芳香族ジヒドロキシ化合物の回収率が悪化し、さらに未反応アルコールの分離、回収に多大なコストがかかることがある。また、モル比が2.4モルより小さいと分解反応速度が遅いか、またはポリカーボネート樹脂が完全に分解されずにカーボネートオリゴマーが残存し易く、芳香族ジヒドロキシ化合物の回収率が低下することがある。 The amount of the alcohol used is preferably 2.4 to 7 mol, more preferably 3 to 7 mol, per 1 mol of the carbonate bond of the aromatic polycarbonate. When the molar ratio is more than 7 moles, the recovery rate of the aromatic dihydroxy compound is deteriorated, and further, the separation and recovery of the unreacted alcohol may be costly. On the other hand, when the molar ratio is less than 2.4 mol, the decomposition reaction rate is slow, or the polycarbonate resin is not completely decomposed and the carbonate oligomer tends to remain, and the recovery rate of the aromatic dihydroxy compound may decrease.
本発明において使用される分解触媒は金属水酸化物である。金属水酸化物の非存在下では分解反応は進行しない。金属水酸化物としては水酸化ナトリウムおよび/または水酸化カリウムが好ましく使用できる。特に水酸化ナトリウムが好ましい。 The cracking catalyst used in the present invention is a metal hydroxide. The decomposition reaction does not proceed in the absence of metal hydroxide. As the metal hydroxide, sodium hydroxide and / or potassium hydroxide can be preferably used. Sodium hydroxide is particularly preferable.
金属水酸化物の使用量は、ポリカーボネートのカーボネート結合1モルに対して0.002〜0.4モルが好ましい。金属水酸化物の使用量が0.002モルより少ないと分解反応速度は大きく低下する。0.4モルより多いと経済的に不利となり、また炭酸ジアルキルの分解が起こり易くなる。 The amount of the metal hydroxide used is preferably 0.002 to 0.4 mol with respect to 1 mol of the carbonate bond of the polycarbonate. When the amount of metal hydroxide used is less than 0.002 mol, the decomposition reaction rate is greatly reduced. When the amount is more than 0.4 mol, it is economically disadvantageous, and the decomposition of the dialkyl carbonate tends to occur.
通常、芳香族ポリカーボネートの製造で用いる金属水酸化物は固形、または水溶液の状態で購入、使用される。反応系内に水が多量に存在すると、触媒と生成した芳香族ジヒドロキシ化合物が反応して塩になり析出し、触媒が消費されてしまい、分解反応が非常に遅くなる。また、回収可能な炭酸ジアルキルの収率が低下する。特に、金属水酸化物の水溶液を使用する場合、反応系内に水分が多くなり易い。反応系内の水を除去する方法としては、有機溶媒と金属水酸化物水溶液を共沸してデカンタで分離する方法、混合液を脱水剤(吸着剤)に通す方法等いくつかの方法が挙げられるが、どの方法で除去しても差し支えない。分解反応を行う前(分解反応初期)の系内(すなわち分解反応処理される溶液中)の水分量は2.5重量%以下が好ましく、1重量%以下がより好ましく、0.5重量%以下がさらに好ましく、特に0.3重量%以下が好ましい。 Usually, the metal hydroxide used in the production of the aromatic polycarbonate is purchased and used in the form of a solid or an aqueous solution. When a large amount of water is present in the reaction system, the catalyst and the generated aromatic dihydroxy compound react to form a salt, which is consumed, and the decomposition reaction becomes very slow. In addition, the yield of recoverable dialkyl carbonate decreases. In particular, when an aqueous solution of metal hydroxide is used, water tends to increase in the reaction system. As a method for removing water in the reaction system, there are several methods such as a method in which an organic solvent and a metal hydroxide aqueous solution are azeotropically separated by a decanter, and a method in which the mixed solution is passed through a dehydrating agent (adsorbent) However, it can be removed by any method. The amount of water in the system (that is, in the solution subjected to the decomposition reaction) before the decomposition reaction (that is, in the solution subjected to the decomposition reaction) is preferably 2.5% by weight or less, more preferably 1% by weight or less, and 0.5% by weight or less. Is more preferable, and 0.3% by weight or less is particularly preferable.
本発明において、分解反応を行う温度は30℃〜90℃が好ましい。30℃未満の場合は分解反応時間が長くなり、処理効率が著しく劣ることがある。また、90℃を越えると、加熱のエネルギーが多く必要となり、さらに分解処理中に溶液の色が褐色に着色し易く、品質の良い芳香族ジヒドロキシ化合物が得られなくなることがある。 In the present invention, the temperature at which the decomposition reaction is performed is preferably 30 ° C to 90 ° C. When it is less than 30 ° C., the decomposition reaction time becomes long, and the processing efficiency may be remarkably inferior. If the temperature exceeds 90 ° C., a large amount of heating energy is required, and the color of the solution tends to turn brown during the decomposition treatment, and a high-quality aromatic dihydroxy compound may not be obtained.
分解反応中に生成した芳香族ジヒドロキシ化合物は、塩基性条件下では酸化されやすいので、反応溶液中に酸化防止剤を添加することが好ましい。また、反応器中の酸素濃度を窒素などの不活性ガスにより、低減しておくことも有効である。 Since the aromatic dihydroxy compound produced during the decomposition reaction is easily oxidized under basic conditions, it is preferable to add an antioxidant to the reaction solution. It is also effective to reduce the oxygen concentration in the reactor with an inert gas such as nitrogen.
酸化防止剤として、重亜硫酸ナトリウム(Na2S2O5)、亜硫酸ナトリウム(Na2SO3)、ハイドロサルファイトナトリウム(Na2S2O4)等が挙げられる。これらを1種または2種以上混合して用いても差し支えない。酸化防止剤の使用量は芳香族ポリカーボネート100重量部に対し、0.05〜4.0重量部が好ましい。0.05〜4.0重量部の範囲であると酸化防止効果があり、また、コスト的に有利で、分解反応速度が低下せず好ましい。
不活性ガスの種類として、窒素、アルゴン等が挙げられる。窒素がコスト的に有利であり好ましい。
Examples of the antioxidant include sodium bisulfite (Na 2 S 2 O 5 ), sodium sulfite (Na 2 SO 3 ), and sodium hydrosulfite (Na 2 S 2 O 4 ). These may be used alone or in combination of two or more. As for the usage-amount of antioxidant, 0.05-4.0 weight part is preferable with respect to 100 weight part of aromatic polycarbonate. If it is in the range of 0.05 to 4.0 parts by weight, it has an antioxidant effect, is advantageous in terms of cost, and is preferable because the decomposition reaction rate does not decrease.
Nitrogen, argon etc. are mentioned as a kind of inert gas. Nitrogen is preferred because of its cost advantage.
前記ろ液中の芳香族ポリカーボネートを炭素数1〜4のアルコールおよび金属水酸化物の存在下、エステル交換反応により分解反応(解重合反応)させて得られた芳香族ジヒドロキシ化合物は、下記の方法で固型の芳香族ジヒドロキシ化合物として回収し、洗浄することが好ましい。 The aromatic dihydroxy compound obtained by subjecting the aromatic polycarbonate in the filtrate to a decomposition reaction (depolymerization reaction) by transesterification in the presence of an alcohol having 1 to 4 carbon atoms and a metal hydroxide is obtained by the following method. It is preferable to recover and wash as a solid aromatic dihydroxy compound.
固型の芳香族ジヒドロキシ化合物を回収する方法としては、前記分解反応後の反応溶液に酸水溶液を加え、有機溶媒相と水溶液相とを分液し、得られた有機溶媒相から蒸留により固体の芳香族ジヒドロキシ化合物を回収する方法が好ましく採用される。 As a method for recovering the solid aromatic dihydroxy compound, an aqueous acid solution is added to the reaction solution after the decomposition reaction, the organic solvent phase and the aqueous solution phase are separated, and a solid solution is obtained by distillation from the obtained organic solvent phase. A method for recovering the aromatic dihydroxy compound is preferably employed.
分解反応後の反応溶液に酸水溶液を加えることにより、芳香族ジヒドロキシ化合物は有機溶媒相に溶解する。酸水溶液としては塩酸、硫酸、硝酸またはリン酸等の無機酸の水溶液が好ましく用いられる。加える酸水溶液の量は、水溶液相が中性〜酸性になるような量が必要であり、中性のpH6〜8の範囲になるような量が特に好ましい。酸を加えずに水を加えると炭酸ジアルキルの加水分解が起こり、さらに芳香族ジヒドロキシ化合物が金属水酸化物と反応して塩になり、芳香族ジヒドロキシ化合物の収率が低下することとなる。また、分解反応後の反応溶液から溶媒を除去すると、芳香族ジヒドロキシ化合物が金属水酸化物と反応して塩になり、着色成分が発生する。このため、着色成分を除去する工程が必要になり、不利な方法となる。 By adding an acid aqueous solution to the reaction solution after the decomposition reaction, the aromatic dihydroxy compound is dissolved in the organic solvent phase. As the acid aqueous solution, an aqueous solution of an inorganic acid such as hydrochloric acid, sulfuric acid, nitric acid or phosphoric acid is preferably used. The amount of the acid aqueous solution to be added needs to be such that the aqueous solution phase is neutral to acidic, and is particularly preferably such that the pH is in the neutral pH range of 6 to 8. When water is added without adding an acid, hydrolysis of the dialkyl carbonate occurs, and the aromatic dihydroxy compound reacts with the metal hydroxide to form a salt, thereby reducing the yield of the aromatic dihydroxy compound. When the solvent is removed from the reaction solution after the decomposition reaction, the aromatic dihydroxy compound reacts with the metal hydroxide to form a salt, and a colored component is generated. For this reason, the process of removing a coloring component is needed and it becomes a disadvantageous method.
分解反応後の反応溶液に酸水溶液を加えると有機溶媒相と水溶液相とに分離する。デカンター等の液液分離器や遠心分離機を使用することにより、有機溶媒相と水溶液相とを分液し、有機溶媒相を得ることができる。分液が不十分であると、有機溶媒相に粒状に浮遊している水が次の工程に混入し、得られる芳香族ジヒドロキシ化合物の純度に影響を及ぼすので、有機溶媒相をさらに純水と接触させ、可能な限り除去することが好ましい。この方法は、洗浄塔による接触、撹拌機、液液分離器による分離、遠心分離機など、公知の方法が使用できる。なお、有機溶媒相と水溶液相とを分離せずにそのまま溶媒を除去すると、芳香族ジヒドロキシ化合物が金属水酸化物と反応して塩になり、着色成分が発生する。このため、着色成分を除去する工程が必要になり、不利な方法となる。 When an aqueous acid solution is added to the reaction solution after the decomposition reaction, it is separated into an organic solvent phase and an aqueous solution phase. By using a liquid-liquid separator such as a decanter or a centrifuge, the organic solvent phase and the aqueous solution phase can be separated to obtain an organic solvent phase. If the liquid separation is insufficient, water suspended in a granular form in the organic solvent phase is mixed in the next step and affects the purity of the resulting aromatic dihydroxy compound. It is preferable to contact and remove as much as possible. As this method, a known method such as contact with a washing tower, separation with a stirrer, liquid-liquid separator, or centrifugal separator can be used. If the solvent is removed as it is without separating the organic solvent phase and the aqueous solution phase, the aromatic dihydroxy compound reacts with the metal hydroxide to form a salt, and a colored component is generated. For this reason, the process of removing a coloring component is needed and it becomes a disadvantageous method.
有機溶媒相から固体の芳香族ジヒドロキシ化合物を回収する方法としては、蒸留により有機溶媒、未反応アルコールおよびジアルキルカーボネートと芳香族ジヒドロキシ化合物とを分離する方法が好ましく採用される。 As a method for recovering the solid aromatic dihydroxy compound from the organic solvent phase, a method of separating the organic solvent, unreacted alcohol and dialkyl carbonate from the aromatic dihydroxy compound by distillation is preferably employed.
蒸留操作は減圧または常圧で行われ、その方法はバッチ式でも連続式でもよいが、芳香族ジヒドロキシ化合物を析出させるためにはバッチ式の方が好ましい。蒸留は有機溶媒、未反応アルコールおよびジアルキルカーボネートが留去できる温度、圧力条件が必要とされるが、芳香族ジヒドロキシ化合物の熱分解を抑えるため、蒸留温度(蒸留槽ボトム温度)は100℃以下とすることが好ましい。また、蒸留槽に不活性ガスを流して、留去しやすくしてもよい。 The distillation operation is carried out under reduced pressure or atmospheric pressure, and the method may be either batch type or continuous type, but batch type is preferred for precipitation of the aromatic dihydroxy compound. Distillation requires a temperature and pressure conditions at which the organic solvent, unreacted alcohol and dialkyl carbonate can be distilled off, but in order to suppress thermal decomposition of the aromatic dihydroxy compound, the distillation temperature (distillation tank bottom temperature) is 100 ° C. or less. It is preferable to do. Alternatively, an inert gas may be flowed through the distillation tank to facilitate the distillation.
なお、蒸留操作により分離して得られた芳香族ジヒドロキシ化合物は微量の未反応アルコール、ジアルキルカーボネート、モノヒドロキシ化合物(末端停止剤)、ポリカーボネート由来の炭酸塩および金属水酸化物と酸水溶液が反応して生成した中性塩等の不純物を含んでおり、これらの化合物は除去することが好ましい。これらの不純物を除去するために、芳香族ジヒドロキシ化合物をハロゲン化炭化水素化合物有機溶媒及び/又は水で洗浄する方法が採用される。 The aromatic dihydroxy compound obtained by separation by distillation operation is a reaction between a trace amount of unreacted alcohol, dialkyl carbonate, monohydroxy compound (terminal terminator), polycarbonate-derived carbonate and metal hydroxide and an aqueous acid solution. It is preferable that these compounds be removed because they contain impurities such as neutral salts produced. In order to remove these impurities, a method of washing the aromatic dihydroxy compound with a halogenated hydrocarbon compound organic solvent and / or water is employed.
ハロゲン化炭化水素化合物有機溶媒としては、25℃における芳香族ジヒドロキシ化合物の溶解度が20g/L以下で、25℃における芳香族モノヒドロキシ化合物(末端停止剤)の溶解度が50g/L以上である溶媒が好ましく、具体的にはジクロロメタン、クロロホルム、ジクロロエタン、トリクロロエタン、テトラクロロエタン、ジクロロエチレン等が好ましく、ジクロロメタン(塩化メチレン)が特に好ましく用いられる。水は50μS/cm以下の電気伝導度の純水を用いることが好ましい。 Examples of the halogenated hydrocarbon compound organic solvent include a solvent in which the solubility of the aromatic dihydroxy compound at 25 ° C. is 20 g / L or less and the solubility of the aromatic monohydroxy compound (terminal stopper) at 25 ° C. is 50 g / L or more. Specifically, dichloromethane, chloroform, dichloroethane, trichloroethane, tetrachloroethane, dichloroethylene and the like are preferable, and dichloromethane (methylene chloride) is particularly preferably used. It is preferable to use pure water having an electric conductivity of 50 μS / cm or less.
洗浄の方法は、固体の芳香族ジヒドロキシ化合物を攪拌槽に移し、有機溶媒と水を同時または別々に投入し、攪拌、ろ過する方法、遠心分離機内で有機溶媒と水を同時または交互に振りかけそのまま遠心分離で脱液する方法等が挙げられる。ジアルキルカーボネートやモノヒドロキシ化合物は有機溶媒相に抽出され、未反応アルコールや塩は水相に抽出され芳香族ジヒドロキシ化合物の純度が向上する。 The washing method is a method in which a solid aromatic dihydroxy compound is transferred to a stirring tank, and an organic solvent and water are added simultaneously or separately, followed by stirring and filtering. The organic solvent and water are sprinkled simultaneously or alternately in a centrifuge. Examples include a method of removing liquid by centrifugation. Dialkyl carbonates and monohydroxy compounds are extracted into the organic solvent phase, and unreacted alcohols and salts are extracted into the aqueous phase to improve the purity of the aromatic dihydroxy compound.
有機溶媒で洗浄する場合、一度の洗浄時間は1分〜60分の範囲が好ましく、洗浄温度は5〜40℃の範囲が好ましい。一度の洗浄に使用する有機溶媒の量は、芳香族ジヒドロキシ化合物100重量部に対して好ましくは50〜1000重量部、より好ましくは100〜500重量部である。 When washing with an organic solvent, the washing time for one time is preferably in the range of 1 minute to 60 minutes, and the washing temperature is preferably in the range of 5 to 40 ° C. The amount of the organic solvent used for one-time washing is preferably 50 to 1000 parts by weight, more preferably 100 to 500 parts by weight with respect to 100 parts by weight of the aromatic dihydroxy compound.
水で洗浄する場合、一度の洗浄時間は1〜60分の範囲が好ましく、洗浄温度は5〜80℃の範囲が好ましい。一度の洗浄に使用する水の量は、芳香族ジヒドロキシ化合物100重量部に対して好ましくは50〜1000重量部、より好ましくは100〜500重量部である。 When washing with water, the time for one washing is preferably in the range of 1 to 60 minutes, and the washing temperature is preferably in the range of 5 to 80 ° C. The amount of water used for one-time washing is preferably 50 to 1000 parts by weight, more preferably 100 to 500 parts by weight with respect to 100 parts by weight of the aromatic dihydroxy compound.
また、洗浄される芳香族ジヒドロキシ化合物は、その平均粒径(重量平均粒子径)が好ましくは100〜1000μm、より好ましくは100〜800μm、特に好ましくは200〜600μmである。前記範囲の平均粒径の芳香族ジヒドロキシ化合物を使用すると効率良く洗浄できるため好ましい。 The aromatic dihydroxy compound to be washed preferably has an average particle size (weight average particle size) of 100 to 1000 μm, more preferably 100 to 800 μm, and particularly preferably 200 to 600 μm. Use of an aromatic dihydroxy compound having an average particle diameter in the above range is preferable because it can be efficiently washed.
得られた固形の芳香族ジヒドロキシ化合物は、芳香族ポリカーボネートの製造工程に原料として再使用することができる。再使用する方法としては、溶融重合法ではそのまま使用することができ、また、界面重合法では金属水酸化物水溶液に所望の濃度で溶解し、芳香族ポリカーボネートの製造に使用することが可能である。その際、芳香族ジヒドロキシ化合物を金属水酸化物水溶液に溶解した溶液を加熱し、残存する有機溶媒を揮発したものを使用することも好ましい。 The obtained solid aromatic dihydroxy compound can be reused as a raw material in the production process of an aromatic polycarbonate. As a re-use method, it can be used as it is in the melt polymerization method, and in the interfacial polymerization method, it can be dissolved in a metal hydroxide aqueous solution at a desired concentration and used for the production of an aromatic polycarbonate. . At that time, it is also preferable to use a solution obtained by heating a solution obtained by dissolving an aromatic dihydroxy compound in a metal hydroxide aqueous solution and volatilizing the remaining organic solvent.
また、本発明で得られた芳香族ジヒドロキシ化合物と市販の芳香族ジヒドロキシ化合物とを一緒に芳香族ポリカーボネートの製造原料として使用しても構わない。回収した芳香族ジヒドロキシ化合物と市販の芳香族ジヒドロキシ化合物を混合する方法は、固体同士、固体と液体、液体同士を混合する方法のどの方法であってもよい。 In addition, the aromatic dihydroxy compound obtained in the present invention and a commercially available aromatic dihydroxy compound may be used together as a raw material for producing an aromatic polycarbonate. The method for mixing the recovered aromatic dihydroxy compound and the commercially available aromatic dihydroxy compound may be any method of solids, solids and liquids, or liquids.
一方、芳香族ポリカーボネートを分解して得られるジアルキルカーボネートを回収する方法としては、前記分液して得られた水溶液相から未反応アルコールとジアルキルカーボネートとをそれぞれ回収し、また、有機溶媒相から蒸発させた留分から有機溶媒、未反応アルコールおよびジアルキルカーボネートをそれぞれ回収する方法が好ましい。その操作方法としては、抽出法や蒸留法が挙げられ、蒸留法が好ましく用いられる。 On the other hand, as a method for recovering the dialkyl carbonate obtained by decomposing the aromatic polycarbonate, unreacted alcohol and dialkyl carbonate are recovered from the aqueous solution phase obtained by the liquid separation and evaporated from the organic solvent phase. A method of recovering the organic solvent, the unreacted alcohol and the dialkyl carbonate from the fraction obtained is preferable. Examples of the operation method include an extraction method and a distillation method, and the distillation method is preferably used.
回収した炭酸ジアルキルは溶融重合法による芳香族ポリカーボネートの製造工程の原材料等に使用できる。また、回収された塩素化合物有機溶媒やアルコールは、ポリカーボネート樹脂の分解反応に再使用することが可能である。 The recovered dialkyl carbonate can be used as a raw material for the production process of an aromatic polycarbonate by a melt polymerization method. The recovered chlorine compound organic solvent and alcohol can be reused in the decomposition reaction of the polycarbonate resin.
本発明の方法で回収した芳香族ジヒドロキシ化合物を原料として用いて得られるポリカーボネート樹脂は、色相および熱安定性に優れることから、例えば光磁気ディスク、各種追記型ディスク、デジタルオーディオディスク(いわゆるコンパクトディスク)、光学式ビデオディスク(いわゆるレーザディスク)、デジタル・バーサイル・ディスク(DVD)等の光学ディスク基板用の材料として、あるいはシリコンウエハー等の精密機材収納容器の材料として好適に使用でき、殊に光学ディスク基板用の材料として好適に採用される。 Since the polycarbonate resin obtained by using the aromatic dihydroxy compound recovered by the method of the present invention as a raw material is excellent in hue and thermal stability, for example, a magneto-optical disc, various write-once discs, a digital audio disc (so-called compact disc) It can be suitably used as a material for an optical disk substrate such as an optical video disk (so-called laser disk) or a digital versatile disk (DVD), or as a material for a precision equipment container such as a silicon wafer. It is suitably employed as a substrate material.
本発明によれば、廃ポリカーボネート樹脂溶液をろ過して得られたろ液を分解反応に使用することにより、分解時間が短く、エネルギーコストも高くない方法で、高品質の芳香族ジヒドロキシ化合物が得られ、この芳香族ジヒドロキシ化合物は芳香族ポリカーボネート製造の原材料として再利用できる。したがって、本発明の奏する工業的効果は格別である。 According to the present invention, by using the filtrate obtained by filtering the waste polycarbonate resin solution for the decomposition reaction, a high-quality aromatic dihydroxy compound can be obtained by a method in which the decomposition time is short and the energy cost is not high. The aromatic dihydroxy compound can be reused as a raw material for producing an aromatic polycarbonate. Therefore, the industrial effect produced by the present invention is exceptional.
以下に実施例を挙げて本発明を更に説明するが、本発明はこれに限定されるものではない。特に断り書きのない場合、部は重量部を表す。なお、評価は次に示す方法で行った。
(1)色相(b値)
ポリカーボネート樹脂ペレットを射出成形機(日本製鋼所(株)製:日鋼アンカー V−17−65型)を用い、シリンダー温度340℃で、厚さ2mmの50mm角板を成形した。その成形板を色差計(日本電色(株)製)を用いてb値を測定した。
EXAMPLES The present invention will be further described below with reference to examples, but the present invention is not limited to these. Unless indicated otherwise, parts represent parts by weight. The evaluation was performed by the following method.
(1) Hue (b value)
Using a polycarbonate resin pellet, a 50 mm square plate having a thickness of 2 mm was molded at a cylinder temperature of 340 ° C. using an injection molding machine (manufactured by Nippon Steel Works, Ltd .: Nikko Anchor V-17-65 type). The molded plate was measured for b value using a color difference meter (manufactured by Nippon Denshoku Co., Ltd.).
(2)熱安定性(△E)
ポリカーボネート樹脂ペレットを射出成形機(日本製鋼所(株)製:日鋼アンカー V−17−65型)を用い、シリンダー温度340℃で10分間滞留させたものとさせないものの試験片(厚さ2mmの50mm角板)をそれぞれ作成し、その色相の変化(△E)を測定した。色相の変化は、色差計(日本電色(株)製)でそれぞれのL、a、b値を測定し、下記式を用いて算出した。
ΔE=[(L′−L)2+(a′−a)2+(b′−b)2]1/2
(L、a、bは滞留させないもの、L′、a′、b′は10分間滞留させたもの)
(2) Thermal stability (△ E)
Test pieces (thickness 2 mm) of polycarbonate resin pellets that were not allowed to stay for 10 minutes at a cylinder temperature of 340 ° C. using an injection molding machine (manufactured by Nippon Steel Co., Ltd .: Nikko Anchor V-17-65 type) 50 mm square plate) was prepared, and the change in hue (ΔE) was measured. The change in hue was calculated using the following formula after measuring the L, a, and b values with a color difference meter (manufactured by Nippon Denshoku Co., Ltd.).
ΔE = [(L′−L) 2 + (a′−a) 2 + (b′−b) 2 ] 1/2
(L, a, b are not retained, L ′, a ′, b ′ are retained for 10 minutes)
(3)ビスフェノールAの純度(有機物中のビスフェノールA純度)
Waters社製高速液体クロマトグラフを用い、サンプル(有機物)0.2gに内部標準としてo−クレゾールを添加したアセトニトリル1mLを加え、溶解し、アセトニトリル/0.2%酢酸水溶液を展開溶媒としてクロマトグラフを得、あらかじめ作成した検量線により、ビスフェノールAの純度を求めた。
(3) Purity of bisphenol A (bisphenol A purity in organic matter)
Using a Waters high performance liquid chromatograph, 0.2 mL of sample (organic matter) was added with 1 mL of acetonitrile with o-cresol added as an internal standard, dissolved, and chromatographed using acetonitrile / 0.2% acetic acid aqueous solution as a developing solvent. The purity of bisphenol A was obtained using a calibration curve prepared in advance.
(4)芳香族ポリカーボネートペレット中の0.5μm以上の異物量
芳香族ポリカーボネートペレット1gを塩化メチレン100mlに溶解させ、微粒子測定器(ハイヤックロイコ社製He−Neレーザー光散乱方式)により0.5μm以上の微粒子数を測定した。
(4) Amount of foreign matter of 0.5 μm or more in aromatic polycarbonate pellet 1 g of aromatic polycarbonate pellet was dissolved in 100 ml of methylene chloride, and 0.5 μm was measured with a fine particle measuring device (He-Ne laser light scattering method manufactured by Hyac Royco). The number of fine particles was measured.
[実施例1]
撹拌槽に市販のコンパクトディスク100部と塩化メチレン600部を投入し、6時間撹拌した。コンパクトディスクの膜は、ポリカーボネートの塩化メチレン溶液中に分散していた。この溶液を孔径5μmのステンレス製フィルターを取り付けたろ過装置(日本ポール社製)に通し、コンパクトディスクの膜(印刷、UV硬化樹脂、アルミ膜等)を除去した。
[Example 1]
100 parts of a commercially available compact disc and 600 parts of methylene chloride were added to the stirring tank and stirred for 6 hours. The compact disc membrane was dispersed in a methylene chloride solution of polycarbonate. This solution was passed through a filtration device (manufactured by Nippon Pole Co., Ltd.) equipped with a stainless steel filter having a pore size of 5 μm to remove the compact disc film (printing, UV curable resin, aluminum film, etc.).
温度計、撹拌機及び還流冷却器、水浴付き反応器に、固体の水酸化ナトリウム4部(芳香族ポリカーボネートのカーボネート結合に対し20モル%)、メタノール80部(芳香族ポリカーボネートのカーボネート結合1モルに対し5モル)、ろ液(ポリカーボネートの塩化メチレン溶液)894部、酸化防止剤としてハイドロサルファイトナトリウム2部を投入し、攪拌した。ここで、系内の溶液の一部をサンプリングして水分量を測定したところ、0.05重量%であった。その後、内温を40℃にするため、水浴を調節した。 To a thermometer, a stirrer, a reflux condenser, and a reactor with a water bath, 4 parts of solid sodium hydroxide (20 mol% with respect to the carbonate bond of the aromatic polycarbonate), 80 parts of methanol (1 mol of the carbonate bond of the aromatic polycarbonate) 5 mol), 894 parts of filtrate (methylene chloride solution of polycarbonate) and 2 parts of hydrosulfite sodium as an antioxidant were added and stirred. Here, when a part of the solution in the system was sampled and the water content was measured, it was 0.05% by weight. Thereafter, the water bath was adjusted to bring the internal temperature to 40 ° C.
反応開始(内温が40℃になって)から4時間後、反応混合物中のカーボネートオリゴマーを1H−NMRで分析したところ、完全に消失しており、メタノール/ジメチルカーボネートのピーク面積比が1.5であり理論量のジメチルカーボネートが生成していることを確認できたので、0.5mol/L塩酸水溶液202部投入し、分解反応を停止させた。 After 4 hours from the start of the reaction (inner temperature reached 40 ° C.), the carbonate oligomer in the reaction mixture was analyzed by 1 H-NMR. As a result, it completely disappeared and the peak area ratio of methanol / dimethyl carbonate was 1 Since it was confirmed that the theoretical amount of dimethyl carbonate was formed, 202 parts of 0.5 mol / L hydrochloric acid aqueous solution was added to stop the decomposition reaction.
分液ロートに反応混合物を移し、有機相949部と水相233部に分離した。水相にはメタノール、ジメチルカーボネート、塩化メチレンが含有されており、これらの有機物は蒸留を繰り返し、それぞれ回収した。蒸留において塩化ナトリウム等の塩分は、水と一緒に廃棄した。 The reaction mixture was transferred to a separatory funnel and separated into 949 parts of an organic phase and 233 parts of an aqueous phase. The aqueous phase contained methanol, dimethyl carbonate and methylene chloride, and these organic substances were recovered by repeated distillation. In distillation, salt such as sodium chloride was discarded together with water.
有機相は40℃の水浴を設けたエバポレータにより減圧して、塩化メチレン、メタノールおよびジメチルカーボネートを除去し、固形分133部を得た。留分からさらに蒸留を繰り返し行い、塩化メチレン、メタノールおよびジメチルカーボネートをそれぞれ分離した。固形分の1H−NMRの分析結果より、ビスフェノールA、p−ターシャリーブチルフェノールおよびジメチルカーボネートが存在していた。青色色素は確認できなかったが、固体が少し青みがかっていた。 The organic phase was depressurized with an evaporator provided with a water bath at 40 ° C. to remove methylene chloride, methanol and dimethyl carbonate to obtain 133 parts of a solid content. Distillation was further repeated from the fraction to separate methylene chloride, methanol and dimethyl carbonate. From the analysis result of solid content of 1 H-NMR, bisphenol A, p-tertiary butylphenol and dimethyl carbonate were present. Although no blue pigment was observed, the solid was slightly bluish.
この固形分に塩化メチレン200部および純水200部を加え、25℃で30分攪拌してスラリーとした。このスラリーを孔径50μmのステンレス製フィルターでろ過し、塩化メチレン100部を固形分にかけて洗浄した。洗浄後固形分を乾燥したところ、107部のビスフェノールAが得られ、その純度は99.8%であった。 To this solid content, 200 parts of methylene chloride and 200 parts of pure water were added and stirred at 25 ° C. for 30 minutes to form a slurry. The slurry was filtered through a stainless steel filter having a pore size of 50 μm, and 100 parts of methylene chloride was washed over the solid content. When the solid content was dried after washing, 107 parts of bisphenol A was obtained, and its purity was 99.8%.
洗浄後のろ液の有機相は青みがかっており、有機相中にp−ターシャリーブチルフェノール、ジメチルカーボネートおよびビスフェノールA、また水相中にジメチルカーボネートとメタノールが存在していた。有機相から蒸留により塩化メチレンとジメチルカーボネートをそれぞれ回収し、水相から蒸留によりジメチルカーボネートとメタノールをそれぞれ回収した。 The organic phase of the filtrate after washing was bluish, and p-tertiary butylphenol, dimethyl carbonate and bisphenol A were present in the organic phase, and dimethyl carbonate and methanol were present in the aqueous phase. Methylene chloride and dimethyl carbonate were recovered from the organic phase by distillation, and dimethyl carbonate and methanol were recovered from the aqueous phase by distillation.
[実施例2]
実施例1において、孔径5μmのステンレス製フィルターを取り付けたろ過装置に代えて孔径8μmのステンレス製フィルターを取り付けたろ過装置を用いた以外は実施例1と同様の操作を行い固体のビスフェノールAを得た。ビスフェノールAの純度は99.8%であった。
[Example 2]
In Example 1, a solid bisphenol A was obtained by performing the same operation as in Example 1 except that a filter with a stainless steel filter with a pore size of 8 μm was used instead of the filter with a stainless steel filter with a pore size of 5 μm. It was. The purity of bisphenol A was 99.8%.
[実施例3]
実施例1において、孔径5μmのステンレス製フィルターを取り付けたろ過装置に代えて孔径40μmのPET製バック式フィルターでろ過を行った後、孔径8μmのステンレス製フィルターを取り付けたろ過装置を用いた以外は実施例1と同様の操作を行い固体のビスフェノールAを得た。ビスフェノールAの純度は99.8%であった。
[Example 3]
In Example 1, after filtering with a PET back filter with a pore size of 40 μm instead of a filtration device with a stainless steel filter with a pore size of 5 μm, a filtration device with a stainless steel filter with a pore size of 8 μm was used. The same operation as in Example 1 was performed to obtain solid bisphenol A. The purity of bisphenol A was 99.8%.
[比較例1]
実施例1において、孔径5μmのステンレス製フィルターを取り付けたろ過装置を使用せずに、コンパクトディスクの膜がポリカーボネートの塩化メチレン溶液に分散した溶液をそのまま分解反応に使用した以外は実施例1と同様の操作を行い固体のビスフェノールAを得た。ビスフェノールAの純度は99.3%であった。
[Comparative Example 1]
Example 1 was the same as Example 1 except that the solution in which the membrane of the compact disc was dispersed in a methylene chloride solution of polycarbonate was used as it was for the decomposition reaction without using a filtration device equipped with a stainless steel filter having a pore size of 5 μm. Thus, solid bisphenol A was obtained. The purity of bisphenol A was 99.3%.
[参考例1] ポリカーボネート樹脂の製造
(A)温度計、撹拌機、還流冷却器、循環器付き反応器に、イオン交換水650部、25%水酸化ナトリウム水溶液252部を仕込み、これに購入した市販のビスフェノールA170部、塩化メチレン13部およびハイドロサルファイト0.34部を加え、循環しながら温度を30℃に保持し40分間で溶解し、ビスフェノールA水溶液を調製した。
[Reference Example 1] Production of polycarbonate resin (A) A thermometer, a stirrer, a reflux condenser, and a reactor with a circulator were charged with 650 parts of ion-exchanged water and 252 parts of a 25% aqueous sodium hydroxide solution and purchased. 170 parts of commercially available bisphenol A, 13 parts of methylene chloride, and 0.34 part of hydrosulfite were added, and the temperature was kept at 30 ° C. while circulating and dissolved in 40 minutes to prepare a bisphenol A aqueous solution.
(B)温度計、撹拌機及び還流冷却器付き反応器に、前記(A)の方法で調製したビスフェノールA水溶液367部を仕込み、塩化メチレン181部を加え、撹拌下15〜25℃でホスゲン28.3部を40分間を要して吹込んだ。ホスゲン吹き込み終了後、48%水酸化ナトリウム水溶液7.2部および固体のp−ターシャリーブチルフェノール1.55部を加え、乳化せしめた後、10分後にトリエチルアミン0.06部を加え、さらに28〜33℃で1時間撹拌して反応を終了した。反応終了後生成物に塩化メチレン400部を加え混合した後、攪拌を停止し、水相と有機相とを分離して、ポリカーボネート樹脂濃度14.5重量%の有機溶媒溶液を得た。(この操作を、反応機2機を用いて繰り返し行った。) (B) A thermometer, a stirrer and a reactor equipped with a reflux condenser were charged with 367 parts of the aqueous bisphenol A solution prepared by the method (A), 181 parts of methylene chloride was added, and phosgene 28 was stirred at 15 to 25 ° C. .3 parts were blown in over 40 minutes. After completion of the phosgene blowing, 7.2 parts of a 48% aqueous sodium hydroxide solution and 1.55 parts of solid p-tertiary butylphenol were added and emulsified. After 10 minutes, 0.06 part of triethylamine was added, and further 28 to 33 The reaction was terminated by stirring for 1 hour at ° C. After completion of the reaction, 400 parts of methylene chloride was added to and mixed with the product, the stirring was stopped, and the aqueous phase and the organic phase were separated to obtain an organic solvent solution having a polycarbonate resin concentration of 14.5% by weight. (This operation was repeated using two reactors.)
この有機溶媒溶液に水150部を加えて攪拌混合した後、攪拌を停止し、水相と有機相とを分離した。この有機相にpH3の塩酸水200部を加え、攪拌混合しトリエチルアミンを抽出した後、攪拌を停止し、水相と有機相とを分離した。次いでさらに分離した有機相にイオン交換水200部を加え攪拌混合した後、攪拌を停止し、水相と有機相とを分離した。この操作を水相の導電率がイオン交換水と殆ど同じになるまで(4回)繰り返した。得られた精製ポリカーボネート樹脂溶液をSUS304製の孔径1μmのフィルターで濾過した。 After adding 150 parts of water to this organic solvent solution and stirring and mixing, stirring was stopped and the aqueous phase and the organic phase were separated. To this organic phase, 200 parts of aqueous hydrochloric acid having a pH of 3 was added and mixed by stirring to extract triethylamine. Then, stirring was stopped and the aqueous phase and the organic phase were separated. Next, 200 parts of ion-exchanged water was added to the separated organic phase, and the mixture was stirred and mixed. Then, the stirring was stopped, and the aqueous phase and the organic phase were separated. This operation was repeated (four times) until the conductivity of the aqueous phase was almost the same as that of ion-exchanged water. The obtained purified polycarbonate resin solution was filtered through a filter made of SUS304 having a pore size of 1 μm.
次に、該有機溶媒溶液を軸受け部に異物取出口を有する隔離室を設けた内壁の材質がSUS316L製の1000Lニーダーにイオン交換水100Lとともに投入し、水温42℃にて塩化メチレンを蒸発させて粉粒体とし、該粉粒体と水の混合物を水温95℃にコントロールされた攪拌機付熱水処理槽に投入し、粉粒体25部対水75部の混合比で30分間攪拌混合した。この粉粒体と水の混合物を遠心分離機で分離して塩化メチレン0.5重量%と水45重量%を含有する粉粒体を得た。この粉粒体を140℃にコントロールされているSUS316L製伝導受熱式溝型2軸攪拌連続乾燥機に50kg/h(ポリカーボネート樹脂換算)で連続供給して、平均乾燥時間3時間の条件で乾燥して粉粒体を得た。 Next, the organic solvent solution was put together with 100 L of ion-exchanged water into a 1000 L kneader made of SUS316L with an inner wall provided with an isolation chamber having a foreign matter outlet at the bearing, and methylene chloride was evaporated at a water temperature of 42 ° C. The mixture was added to a hydrothermal treatment tank with a stirrer controlled at a water temperature of 95 ° C., and stirred and mixed for 30 minutes at a mixing ratio of 25 parts of powder and 75 parts of water. This mixture of powder and water was separated with a centrifuge to obtain a powder containing 0.5% by weight of methylene chloride and 45% by weight of water. This granular material is continuously fed at 50 kg / h (converted to polycarbonate resin) to a conductive heat receiving groove type biaxial stirring continuous dryer made of SUS316L controlled at 140 ° C. and dried under the condition of an average drying time of 3 hours. To obtain a granular material.
この粉粒体100重量部にトリス(2,4−ジ−tert−ブチルフェニル)ホスファイトを0.01重量部、4,4’−ビフェニレンジホスホスフィン酸テトラキス(2,4−ジ−tert−ブチルフェニル)を0.01重量部およびステアリン酸モノグリセリドを0.08重量部加え混合した。かかる粉粒体をベント式二軸押出機[東芝機械(株)製TEM−50B]によりシリンダー温度280℃、乾式真空ポンプを用いてベント吸引圧700Paで吸引脱気しながら溶融混練押出し、ペレットを得た。得られたペレットを用いて異物量、色相(b値)および熱安定性(ΔE)を評価し、その結果を表1に示した。 0.01 parts by weight of tris (2,4-di-tert-butylphenyl) phosphite and 4,4′-biphenylenediphosphosphinic acid tetrakis (2,4-di-tert- Butylphenyl) and 0.018 parts by weight of stearic acid monoglyceride were added and mixed. Such a powder is melt-kneaded and extruded by a vent type twin screw extruder [TEM-50B manufactured by Toshiba Machine Co., Ltd.] with a cylinder temperature of 280 ° C. and a suction vacuum of 700 Pa using a dry vacuum pump. Obtained. The obtained pellets were used to evaluate the amount of foreign matter, hue (b value), and thermal stability (ΔE). The results are shown in Table 1.
[実施例4]
参考例1(A)において、市販のビスフェノールAの代わりに実施例1で得られたビスフェノールAを使用すること以外は、参考例1と同様な操作を行いペレットを得た。得られたペレットを用いて異物量、色相(b値)および熱安定性(ΔE)を評価し、その結果を表1に示した。
[Example 4]
In Reference Example 1 (A), a pellet was obtained by performing the same operation as in Reference Example 1 except that bisphenol A obtained in Example 1 was used instead of commercially available bisphenol A. The obtained pellets were used to evaluate the amount of foreign matter, hue (b value), and thermal stability (ΔE). The results are shown in Table 1.
[実施例5]
参考例1(A)において、市販のビスフェノールAの代わりに実施例2で得られたビスフェノールAを使用すること以外は、参考例1と同様な操作を行いペレットを得た。得られたペレットを用いて異物量、色相(b値)および熱安定性(ΔE)を評価し、その結果を表1に示した。
[Example 5]
In Reference Example 1 (A), a pellet was obtained by performing the same operation as in Reference Example 1 except that bisphenol A obtained in Example 2 was used instead of commercially available bisphenol A. The obtained pellets were used to evaluate the amount of foreign matter, hue (b value), and thermal stability (ΔE). The results are shown in Table 1.
[実施例6]
参考例1(A)において、市販のビスフェノールAの代わりに実施例3で得られたビスフェノールAを使用すること以外は、参考例1と同様な操作を行いペレットを得た。得られたペレットを用いて異物量、色相(b値)および熱安定性(ΔE)を評価し、その結果を表1に示した。
[Example 6]
In Reference Example 1 (A), a pellet was obtained by performing the same operation as in Reference Example 1 except that bisphenol A obtained in Example 3 was used instead of commercially available bisphenol A. The obtained pellets were used to evaluate the amount of foreign matter, hue (b value), and thermal stability (ΔE). The results are shown in Table 1.
[比較例2]
参考例1(A)において、市販のビスフェノールAの代わりに比較例1で得られたビスフェノールAを使用すること以外は、参考例1と同様な操作を行いペレットを得た。得られたペレットを用いて異物量、色相(b値)および熱安定性(ΔE)を評価し、その結果を表1に示した。
[Comparative Example 2]
In Reference Example 1 (A), a pellet was obtained by performing the same operation as in Reference Example 1 except that bisphenol A obtained in Comparative Example 1 was used instead of commercially available bisphenol A. The obtained pellets were used to evaluate the amount of foreign matter, hue (b value), and thermal stability (ΔE). The results are shown in Table 1.
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