JP2003128600A - Method for producing terephthalic acid from waste bottle - Google Patents
Method for producing terephthalic acid from waste bottleInfo
- Publication number
- JP2003128600A JP2003128600A JP2001317884A JP2001317884A JP2003128600A JP 2003128600 A JP2003128600 A JP 2003128600A JP 2001317884 A JP2001317884 A JP 2001317884A JP 2001317884 A JP2001317884 A JP 2001317884A JP 2003128600 A JP2003128600 A JP 2003128600A
- Authority
- JP
- Japan
- Prior art keywords
- pet
- dmt
- terephthalic acid
- tank
- water
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Pending
Links
- KKEYFWRCBNTPAC-UHFFFAOYSA-N Terephthalic acid Chemical compound OC(=O)C1=CC=C(C(O)=O)C=C1 KKEYFWRCBNTPAC-UHFFFAOYSA-N 0.000 title claims abstract description 153
- 239000002699 waste material Substances 0.000 title claims abstract description 29
- 238000004519 manufacturing process Methods 0.000 title claims description 14
- WOZVHXUHUFLZGK-UHFFFAOYSA-N dimethyl terephthalate Chemical compound COC(=O)C1=CC=C(C(=O)OC)C=C1 WOZVHXUHUFLZGK-UHFFFAOYSA-N 0.000 claims abstract description 162
- LYCAIKOWRPUZTN-UHFFFAOYSA-N Ethylene glycol Chemical compound OCCO LYCAIKOWRPUZTN-UHFFFAOYSA-N 0.000 claims abstract description 152
- OKKJLVBELUTLKV-UHFFFAOYSA-N Methanol Chemical compound OC OKKJLVBELUTLKV-UHFFFAOYSA-N 0.000 claims abstract description 132
- 229920000139 polyethylene terephthalate Polymers 0.000 claims abstract description 89
- 239000005020 polyethylene terephthalate Substances 0.000 claims abstract description 89
- 238000000034 method Methods 0.000 claims abstract description 31
- 238000006460 hydrolysis reaction Methods 0.000 claims abstract description 28
- -1 polyethylene terephthalate Polymers 0.000 claims abstract description 22
- 238000005809 transesterification reaction Methods 0.000 claims abstract description 20
- 239000012535 impurity Substances 0.000 claims abstract description 14
- 239000000843 powder Substances 0.000 claims abstract description 12
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims description 61
- 239000007788 liquid Substances 0.000 claims description 40
- 238000004821 distillation Methods 0.000 claims description 26
- 229920005989 resin Polymers 0.000 claims description 26
- 239000011347 resin Substances 0.000 claims description 26
- 229920000642 polymer Polymers 0.000 claims description 22
- 238000001816 cooling Methods 0.000 claims description 16
- LPNBBFKOUUSUDB-UHFFFAOYSA-N p-toluic acid Chemical compound CC1=CC=C(C(O)=O)C=C1 LPNBBFKOUUSUDB-UHFFFAOYSA-N 0.000 claims description 16
- WPYMKLBDIGXBTP-UHFFFAOYSA-N benzoic acid Chemical compound OC(=O)C1=CC=CC=C1 WPYMKLBDIGXBTP-UHFFFAOYSA-N 0.000 claims description 15
- 239000003054 catalyst Substances 0.000 claims description 15
- 239000000203 mixture Substances 0.000 claims description 15
- 238000000926 separation method Methods 0.000 claims description 15
- 239000004698 Polyethylene Substances 0.000 claims description 12
- CDBYLPFSWZWCQE-UHFFFAOYSA-L Sodium Carbonate Chemical compound [Na+].[Na+].[O-]C([O-])=O CDBYLPFSWZWCQE-UHFFFAOYSA-L 0.000 claims description 12
- 238000002156 mixing Methods 0.000 claims description 12
- 229920000573 polyethylene Polymers 0.000 claims description 12
- 239000002002 slurry Substances 0.000 claims description 12
- 239000000126 substance Substances 0.000 claims description 10
- 239000004800 polyvinyl chloride Substances 0.000 claims description 8
- 239000005711 Benzoic acid Substances 0.000 claims description 7
- 235000010233 benzoic acid Nutrition 0.000 claims description 7
- REIDAMBAPLIATC-UHFFFAOYSA-M 4-methoxycarbonylbenzoate Chemical compound COC(=O)C1=CC=C(C([O-])=O)C=C1 REIDAMBAPLIATC-UHFFFAOYSA-M 0.000 claims description 6
- 229910000029 sodium carbonate Inorganic materials 0.000 claims description 6
- 239000004793 Polystyrene Substances 0.000 claims description 5
- 238000003860 storage Methods 0.000 claims description 5
- ZOIORXHNWRGPMV-UHFFFAOYSA-N acetic acid;zinc Chemical compound [Zn].CC(O)=O.CC(O)=O ZOIORXHNWRGPMV-UHFFFAOYSA-N 0.000 claims description 4
- 150000001732 carboxylic acid derivatives Chemical class 0.000 claims description 4
- CJOJIAKIRLKBOO-UHFFFAOYSA-N dimethyl 2-hydroxybenzene-1,4-dicarboxylate Chemical compound COC(=O)C1=CC=C(C(=O)OC)C(O)=C1 CJOJIAKIRLKBOO-UHFFFAOYSA-N 0.000 claims description 4
- 238000001035 drying Methods 0.000 claims description 4
- 229940071125 manganese acetate Drugs 0.000 claims description 4
- UOGMEBQRZBEZQT-UHFFFAOYSA-L manganese(2+);diacetate Chemical compound [Mn+2].CC([O-])=O.CC([O-])=O UOGMEBQRZBEZQT-UHFFFAOYSA-L 0.000 claims description 4
- 239000010409 thin film Substances 0.000 claims description 4
- 239000004246 zinc acetate Substances 0.000 claims description 4
- 230000005484 gravity Effects 0.000 claims description 3
- 238000012856 packing Methods 0.000 claims description 3
- JFFQXJXLNZADOF-UHFFFAOYSA-N 4-ethoxycarbonylbenzenecarboperoxoic acid Chemical compound CCOC(=O)C1=CC=C(C(=O)OO)C=C1 JFFQXJXLNZADOF-UHFFFAOYSA-N 0.000 claims description 2
- 239000007809 chemical reaction catalyst Substances 0.000 claims description 2
- 150000003839 salts Chemical class 0.000 claims description 2
- 239000011734 sodium Substances 0.000 claims description 2
- RPACBEVZENYWOL-XFULWGLBSA-M sodium;(2r)-2-[6-(4-chlorophenoxy)hexyl]oxirane-2-carboxylate Chemical compound [Na+].C=1C=C(Cl)C=CC=1OCCCCCC[C@]1(C(=O)[O-])CO1 RPACBEVZENYWOL-XFULWGLBSA-M 0.000 claims description 2
- QPKOBORKPHRBPS-UHFFFAOYSA-N bis(2-hydroxyethyl) terephthalate Chemical compound OCCOC(=O)C1=CC=C(C(=O)OCCO)C=C1 QPKOBORKPHRBPS-UHFFFAOYSA-N 0.000 claims 3
- DYNFCHNNOHNJFG-UHFFFAOYSA-N 2-formylbenzoic acid Chemical compound OC(=O)C1=CC=CC=C1C=O DYNFCHNNOHNJFG-UHFFFAOYSA-N 0.000 claims 2
- 239000000463 material Substances 0.000 abstract description 10
- 238000005406 washing Methods 0.000 abstract description 9
- 239000002994 raw material Substances 0.000 abstract description 7
- 238000011109 contamination Methods 0.000 abstract description 3
- 238000010298 pulverizing process Methods 0.000 abstract description 2
- 238000006243 chemical reaction Methods 0.000 description 30
- GOUHYARYYWKXHS-UHFFFAOYSA-N 4-formylbenzoic acid Chemical compound OC(=O)C1=CC=C(C=O)C=C1 GOUHYARYYWKXHS-UHFFFAOYSA-N 0.000 description 16
- 238000004064 recycling Methods 0.000 description 12
- 238000012691 depolymerization reaction Methods 0.000 description 9
- 238000011084 recovery Methods 0.000 description 8
- 239000004743 Polypropylene Substances 0.000 description 7
- 239000000047 product Substances 0.000 description 7
- 239000007795 chemical reaction product Substances 0.000 description 6
- 238000004140 cleaning Methods 0.000 description 6
- 229920000728 polyester Polymers 0.000 description 6
- 229920001155 polypropylene Polymers 0.000 description 6
- 229920000915 polyvinyl chloride Polymers 0.000 description 6
- 239000007787 solid Substances 0.000 description 6
- 238000003756 stirring Methods 0.000 description 6
- 238000011282 treatment Methods 0.000 description 6
- 239000003513 alkali Substances 0.000 description 5
- 238000000354 decomposition reaction Methods 0.000 description 4
- 239000000178 monomer Substances 0.000 description 4
- 239000012452 mother liquor Substances 0.000 description 4
- 239000004480 active ingredient Substances 0.000 description 3
- 238000005119 centrifugation Methods 0.000 description 3
- 238000005886 esterification reaction Methods 0.000 description 3
- 239000000835 fiber Substances 0.000 description 3
- 239000010408 film Substances 0.000 description 3
- 238000001914 filtration Methods 0.000 description 3
- 238000004817 gas chromatography Methods 0.000 description 3
- 239000002245 particle Substances 0.000 description 3
- 230000035699 permeability Effects 0.000 description 3
- 229920002223 polystyrene Polymers 0.000 description 3
- 238000012545 processing Methods 0.000 description 3
- GPXYXKPGTHSCRY-UHFFFAOYSA-N 3,4,5-trioxabicyclo[5.2.2]undeca-1(9),7,10-triene-2,6-dione Chemical compound O=C1OOOC(=O)C2=CC=C1C=C2 GPXYXKPGTHSCRY-UHFFFAOYSA-N 0.000 description 2
- IJGRMHOSHXDMSA-UHFFFAOYSA-N Atomic nitrogen Chemical compound N#N IJGRMHOSHXDMSA-UHFFFAOYSA-N 0.000 description 2
- 239000002253 acid Substances 0.000 description 2
- 230000000052 comparative effect Effects 0.000 description 2
- 150000001875 compounds Chemical class 0.000 description 2
- 230000006866 deterioration Effects 0.000 description 2
- 230000000694 effects Effects 0.000 description 2
- 230000032050 esterification Effects 0.000 description 2
- 239000000706 filtrate Substances 0.000 description 2
- 239000007789 gas Substances 0.000 description 2
- 238000004128 high performance liquid chromatography Methods 0.000 description 2
- 230000007062 hydrolysis Effects 0.000 description 2
- 230000003301 hydrolyzing effect Effects 0.000 description 2
- 238000004811 liquid chromatography Methods 0.000 description 2
- 238000002844 melting Methods 0.000 description 2
- 230000008018 melting Effects 0.000 description 2
- 150000002736 metal compounds Chemical group 0.000 description 2
- 239000011259 mixed solution Substances 0.000 description 2
- 239000000049 pigment Substances 0.000 description 2
- 229920003023 plastic Polymers 0.000 description 2
- 239000004033 plastic Substances 0.000 description 2
- 238000006068 polycondensation reaction Methods 0.000 description 2
- 239000002685 polymerization catalyst Substances 0.000 description 2
- 230000009257 reactivity Effects 0.000 description 2
- 239000000243 solution Substances 0.000 description 2
- IIYFAKIEWZDVMP-UHFFFAOYSA-N tridecane Chemical compound CCCCCCCCCCCCC IIYFAKIEWZDVMP-UHFFFAOYSA-N 0.000 description 2
- 238000005292 vacuum distillation Methods 0.000 description 2
- 238000004065 wastewater treatment Methods 0.000 description 2
- UFMBOFGKHIXOTA-UHFFFAOYSA-N 2-methylterephthalic acid Chemical compound CC1=CC(C(O)=O)=CC=C1C(O)=O UFMBOFGKHIXOTA-UHFFFAOYSA-N 0.000 description 1
- 102100024522 Bladder cancer-associated protein Human genes 0.000 description 1
- 101150110835 Blcap gene Proteins 0.000 description 1
- YXHKONLOYHBTNS-UHFFFAOYSA-N Diazomethane Chemical compound C=[N+]=[N-] YXHKONLOYHBTNS-UHFFFAOYSA-N 0.000 description 1
- VEXZGXHMUGYJMC-UHFFFAOYSA-N Hydrochloric acid Chemical compound Cl VEXZGXHMUGYJMC-UHFFFAOYSA-N 0.000 description 1
- 101100493740 Oryza sativa subsp. japonica BC10 gene Proteins 0.000 description 1
- 229920001283 Polyalkylene terephthalate Polymers 0.000 description 1
- 239000000853 adhesive Substances 0.000 description 1
- 230000001070 adhesive effect Effects 0.000 description 1
- 230000002411 adverse Effects 0.000 description 1
- 229910052782 aluminium Inorganic materials 0.000 description 1
- XAGFODPZIPBFFR-UHFFFAOYSA-N aluminium Chemical compound [Al] XAGFODPZIPBFFR-UHFFFAOYSA-N 0.000 description 1
- 239000002585 base Substances 0.000 description 1
- 239000006227 byproduct Substances 0.000 description 1
- 235000014171 carbonated beverage Nutrition 0.000 description 1
- 239000012295 chemical reaction liquid Substances 0.000 description 1
- 239000012141 concentrate Substances 0.000 description 1
- 208000012839 conversion disease Diseases 0.000 description 1
- 238000010586 diagram Methods 0.000 description 1
- BTVWZWFKMIUSGS-UHFFFAOYSA-N dimethylethyleneglycol Natural products CC(C)(O)CO BTVWZWFKMIUSGS-UHFFFAOYSA-N 0.000 description 1
- 239000003651 drinking water Substances 0.000 description 1
- 235000020188 drinking water Nutrition 0.000 description 1
- 239000000975 dye Substances 0.000 description 1
- 239000012467 final product Substances 0.000 description 1
- 235000013305 food Nutrition 0.000 description 1
- 238000000227 grinding Methods 0.000 description 1
- 238000010438 heat treatment Methods 0.000 description 1
- 229910000041 hydrogen chloride Inorganic materials 0.000 description 1
- IXCSERBJSXMMFS-UHFFFAOYSA-N hydrogen chloride Substances Cl.Cl IXCSERBJSXMMFS-UHFFFAOYSA-N 0.000 description 1
- 238000010348 incorporation Methods 0.000 description 1
- 239000011261 inert gas Substances 0.000 description 1
- 230000014759 maintenance of location Effects 0.000 description 1
- 238000005259 measurement Methods 0.000 description 1
- 238000003801 milling Methods 0.000 description 1
- 239000011268 mixed slurry Substances 0.000 description 1
- 230000003472 neutralizing effect Effects 0.000 description 1
- 229910052757 nitrogen Inorganic materials 0.000 description 1
- 230000000704 physical effect Effects 0.000 description 1
- 229920001225 polyester resin Polymers 0.000 description 1
- 239000004645 polyester resin Substances 0.000 description 1
- 229920005672 polyolefin resin Polymers 0.000 description 1
- 238000002203 pretreatment Methods 0.000 description 1
- 238000011002 quantification Methods 0.000 description 1
- 238000012216 screening Methods 0.000 description 1
- 229920006300 shrink film Polymers 0.000 description 1
- 235000014214 soft drink Nutrition 0.000 description 1
- 239000002904 solvent Substances 0.000 description 1
- 235000013555 soy sauce Nutrition 0.000 description 1
- 239000007858 starting material Substances 0.000 description 1
- KKEYFWRCBNTPAC-UHFFFAOYSA-L terephthalate(2-) Chemical compound [O-]C(=O)C1=CC=C(C([O-])=O)C=C1 KKEYFWRCBNTPAC-UHFFFAOYSA-L 0.000 description 1
- 150000003503 terephthalic acid derivatives Chemical class 0.000 description 1
- 238000002834 transmittance Methods 0.000 description 1
- 239000012808 vapor phase Substances 0.000 description 1
- 239000003643 water by type 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)
- Organic Low-Molecular-Weight Compounds And Preparation Thereof (AREA)
- Low-Molecular Organic Synthesis Reactions Using Catalysts (AREA)
Abstract
Description
【0001】[0001]
【発明の属する技術分野】ポリエチレンテレフタレート
(PET)を主成分として含有しさらにそれとは異なる
成分を含有する樹脂ボトル廃棄物を粉砕、洗浄、異物除
去等の前処理を施した後に化学的な反応処理を加え、有
効成分としての高純度のテレフタル酸ジメチルを回収
し、化学反応によって高純度のテレフタル酸を得る方
法、すなわち、回収した使用済みのPETボトルから再
びPETボトル用等のポリマー原料となるテレフタル酸
の製造方法に関する。TECHNICAL FIELD The present invention relates to a chemical reaction treatment after a resin bottle waste containing polyethylene terephthalate (PET) as a main component and a component different from that is subjected to pretreatments such as crushing, washing and removing foreign substances. Is added to recover high-purity dimethyl terephthalate as an active ingredient to obtain high-purity terephthalic acid by a chemical reaction, that is, terephthalate, which is used as a polymer raw material for PET bottles, is recovered from used PET bottles. It relates to a method for producing an acid.
【0002】[0002]
【従来の技術】ポリエチレンテレフタレート(PET)
に代表されるポリアルキレンテレフタレートは、その化
学的安定性に優れていることから、繊維、フィルム、樹
脂などの生活関連資材、飲料水・炭酸飲料用ボトル等の
食品分野等に大量に生産・使用されている。2. Description of the Related Art Polyethylene terephthalate (PET)
The polyalkylene terephthalate represented by is excellent in its chemical stability, so it is produced and used in large quantities in the food field such as life related materials such as fibers, films, resins, and bottles for drinking water and carbonated drinks. Has been done.
【0003】しかしながら、生産量・使用量の増大に伴
って大量に発生する繊維・フィルム・樹脂製品の廃棄
物、規格外品のポリエステルの処理費用は、製造コスト
にも係わってくるのみならず、これらの処理は現在非常
に大きな社会問題となっており、そのリサイクル方法に
ついて各種の提案がなされている。However, the processing costs of waste of fiber / film / resin products and polyester of nonstandard products which are generated in large quantities with the increase of production / usage amount are not only related to the manufacturing cost. These treatments have become a very big social problem at present, and various proposals have been made for their recycling methods.
【0004】特にその廃棄物のなかでも、その嵩高さか
らPETボトルの処理は一層深刻になりつつある。にも
かかわらず、そのリサイクル方法としてはマテリアルリ
サイクルとして、回収された使用済みのPETボトルを
再び溶融して繊維化する程度のリサイクルしか実施され
ておらず、このような単に溶融成型する方法では、その
物性の低下により再びPETボトルとして使用すること
は不可能である。Among the wastes, the processing of PET bottles is becoming more serious due to its bulkiness. Nevertheless, as the recycling method, as material recycling, only the recycling to the extent that the collected used PET bottles are melted again to be fiberized is carried out. It cannot be used again as a PET bottle due to the deterioration of its physical properties.
【0005】一方、PETボトルを洗浄し、再び充填す
るリフィール方法においては、回収費用の負担先や安全
性、衛生性の観点、再使用回数に限度があること、最終
的には廃棄されることになる等、恒久的な対策とは成り
得ないという問題がある。On the other hand, in the refill method of cleaning and refilling PET bottles, the cost of collection, the safety and hygiene viewpoint, the number of reuses is limited, and the PET bottles are eventually discarded. However, there is a problem that it cannot be a permanent measure.
【0006】また、PETボトル屑にはラベル、シュリ
ンクフィルム、ベースカップ、キャップなどの異物樹
脂、ポリ塩化ビニルやポリオレフィン系樹脂等の異ポリ
マー類、キャップ由来のアルミ、接着剤、顔料、染料等
が混入することがある。分別回収されたPETボトル梱
包ベールにも異物材料の混入は避け難いものである。Further, PET bottle scraps include foreign resins such as labels, shrink films, base cups and caps, different polymers such as polyvinyl chloride and polyolefin resins, aluminum derived from caps, adhesives, pigments and dyes. May be mixed. It is unavoidable to mix foreign materials into the PET bottle packing bale that has been separated and collected.
【0007】このようなPETボトル屑を、水やメタノ
ールやエチレングリコールなどの溶媒を用いてPETポ
リマーを構成するモノマーに分解して再利用するケミカ
ルリサイクルにおいても、異物材料は加熱操作、反応操
作の過程で各種分解ガス(例えば塩化水素ガス等)を発
生し、あるいは回収装置内で溶融、固化して、機器類を
損傷したり、化学反応で回収したモノマー(DMT)の
品質を著しく低下させる場合がある。Also in chemical recycling in which such PET bottle waste is decomposed into a monomer constituting a PET polymer using water, a solvent such as methanol or ethylene glycol, and reused, the foreign material is subjected to heating operation and reaction operation. When various decomposition gases (such as hydrogen chloride gas) are generated in the process, or melted and solidified in the recovery device to damage the equipment or significantly deteriorate the quality of the monomer (DMT) recovered by the chemical reaction. There is.
【0008】ケミカルリサイクルの例としては、特開平
11−21374号公報記載のアルカリ化合物の存在下
にポリエステル廃棄物を加水分解してテレフタル酸を得
る方法、WO−97/24310号にも同様にアルカリ
化合物の存在下にポリエステル廃棄物を加水分解して更
に酸で中和してテレフタル酸を得る方法、米国特許第5
952520号明細書記載のメタノール中での気相メタ
ノール分解によりテレフタル酸ジメチルとエチレングリ
コールを得る方法等がある。しかしこれらはいずれも、
200℃以上の高温の反応条件を必要とするため、19
0℃から分解が開始し、その分解物が最終製品の品質悪
化を起こすポリ塩化ビニル等のポリエステルとは異ポリ
マー類の混入に対する許容度が非常に低いという問題が
あった。As an example of chemical recycling, a method of hydrolyzing polyester waste in the presence of an alkaline compound to obtain terephthalic acid, which is described in JP-A-11-21374, and WO-97 / 24310, the alkali is also used. Method of hydrolyzing polyester waste in the presence of compound and further neutralizing with acid to obtain terephthalic acid, US Pat.
There is a method for obtaining dimethyl terephthalate and ethylene glycol by vapor-phase methanol decomposition in methanol described in Japanese Patent No. 952520. But these are all
Since high-temperature reaction conditions of 200 ° C or higher are required, 19
There is a problem that the decomposition starts at 0 ° C., and the decomposition product has a very low tolerance for inclusion of polymers different from polyesters such as polyvinyl chloride, which deteriorates the quality of the final product.
【0009】さらに特開2000−169623号公報
には、ポリエチレンテレフタレート廃棄物をエチレング
リコールで分解し、回収したビス−β−ヒドロキシエチ
ルテレフタレート(BHET)を薄膜蒸発装置により精
製した後にBHETを溶融重縮合させてポリエチレンテ
レフタレートポリマーを得るプロセスが提案されている
が、この場合も200℃以上の熱履歴を課す工程があ
り、ポリ塩化ビニル等の熱分解する異ポリマー類の混入
許容度は低い。すなわち、ケミカルリサイクルにおいて
もマテリアルリサイクルよりは不純物混入の許容度は高
いものの、前処理工程においてほとんど完全に不純物を
除去する必要があった。Further, in Japanese Patent Laid-Open No. 2000-169623, polyethylene terephthalate waste is decomposed with ethylene glycol, and recovered bis-β-hydroxyethyl terephthalate (BHET) is purified by a thin film evaporator, and then BHET is melt polycondensed. A process for obtaining a polyethylene terephthalate polymer has been proposed, but in this case as well, there is a step of imposing a thermal history of 200 ° C. or higher, and the tolerance of incorporation of thermally decomposing different polymers such as polyvinyl chloride is low. That is, although chemical recycling has a higher tolerance of mixing impurities than material recycling, it was necessary to almost completely remove impurities in the pretreatment process.
【0010】一方、ボトル用PETポリマーはジメチル
テレフタレート(DMT)あるいはテレフタル酸(T
A)を出発原料としてエチレングリコール(EG)との
エステル交換反応あるいはエステル化反応でオリゴマー
を得、引続いた重縮合反応で得ることが、一般的に知ら
れているが、その原料DMTあるいはTAは十分に不純
物の少ない高度に精製されたものでなければ、PETボ
トル用として使用できるPETポリマーは得られない。On the other hand, PET polymers for bottles are dimethyl terephthalate (DMT) or terephthalic acid (T
It is generally known that A) is used as a starting material to obtain an oligomer by a transesterification reaction or an esterification reaction with ethylene glycol (EG), followed by a polycondensation reaction. Is not sufficiently purified to obtain a PET polymer usable for PET bottles.
【0011】このような種々の制約があるために、使用
済みのPETボトルをケミカルリサイクル法によって有
効成分を回収し、再びPETボトル用のPETポリマー
原料として使用できるテレフタル酸を得る方法は、これ
までに実用に供し得るものが提案されていないのが実情
である。Due to such various restrictions, the method of recovering an active ingredient from a used PET bottle by a chemical recycling method and obtaining terephthalic acid which can be used again as a PET polymer raw material for a PET bottle has hitherto been known. In reality, there is no proposal for practical use.
【0012】[0012]
【発明が解決しようとする課題】本発明は、上記従来技
術を背景になされたもので、その目的は、PETを主成
分として含有しさらにそれとは異なる成分を含有する樹
脂ボトル廃棄物から、不純物の混入に対しても汚染させ
ることなく高純度のモノマー(DMT)を得、次いで該
高純度DMTからボトル用PETの原料としても好適な
テレフタル酸を効率的に製造できる方法を提供すること
にある。SUMMARY OF THE INVENTION The present invention has been made against the background of the above-mentioned prior art, and its object is to remove impurities from resin bottle waste containing PET as a main component and a component different from PET as impurities. It is an object of the present invention to provide a method capable of obtaining a high-purity monomer (DMT) without being contaminated by the contamination of the above, and then efficiently producing terephthalic acid suitable as a raw material for PET for bottles from the high-purity DMT. .
【0013】[0013]
【課題を解決するための手段】本発明者らは、上記従来
目的を達成するために鋭意検討を行った結果、PETを
主成分として含有しさらにそれとは異なる成分を含有す
る樹脂ボトル廃棄物に粉砕、洗浄、異物除去等の前処理
を施した後、化学的な反応処理を加えて高純度のテレフ
タル酸ジメチルを回収し、さらにそれを加水分解すれば
ボトル用のPETポリマーに適した高純度のテレフタル
酸が得られること、すなわち、例えば回収した使用済み
のPETボトル等の樹脂ボトル廃棄物からボトル用のP
ETポリマーの原料となる高純度テレフタル酸が効率よ
く得られることを見出し、本発明を完成するに至った。Means for Solving the Problems As a result of intensive studies to achieve the above-mentioned conventional objects, the present inventors have found that resin bottle waste containing PET as a main component and a component different from PET After pretreatment such as crushing, washing, and removal of foreign substances, chemical reaction treatment is added to recover high-purity dimethyl terephthalate, which can be further hydrolyzed to obtain high-purity PET polymer suitable for bottles. Of terephthalic acid is obtained, that is, for example, from collected plastic bottle waste such as used PET bottles, P for bottles can be obtained.
The inventors have found that high-purity terephthalic acid, which is a raw material for ET polymer, can be efficiently obtained, and completed the present invention.
【0014】かくして、本発明によれば、「ポリエチレ
ンテレフタレート(PET)を主成分として含有しさら
にそれとは異なる成分を含有する樹脂ボトル廃棄物を、
下記工程(1)〜(19)に順次供することを特徴とす
る、樹脂ボトル廃棄物からのテレフタル酸の製造方法。
(1)分別収集・回収されたPETを主成分として含有
しさらにそれとは異なる成分を含有する樹脂ボトル廃棄
物梱包ベールを解梱包する工程、(2)解梱包した樹脂
ボトル廃棄物を2〜30mm角のフレーク状にする粉砕
工程、(3)フレーク状の樹脂ボトル片からポリエチレ
ン(PE)、ポリスチレン(PS)、ポリ塩化ビニル
(PVC)等からなるラベル薄膜フィルムなどのPET
と異なる成分ポリマーを風力選別により分離する工程、
(4)樹脂ボトル内外の異物及び/又は樹脂ボトル内の
中身残渣を水により洗浄することと、水よりも比重の小
さいPE、PP等の異成分ポリマーを分離することを兼
ねたデカンター工程、(5)回収PETフレークスをフ
レークス保管槽へ送る空送工程、(6)回収PETフレ
ークスをPET解重合触媒を含むエチレングリコール
(EG)中に投入して175℃〜190℃の温度、0.
1〜0.5MPaの圧力下において処理し、ビス−β−
ヒドロキシエチルテレフタレート(BHET)を得るP
ET解重合工程、(7)EGに溶解しない成分の固液分
離工程、(8)液中の粗BHET中のEG成分を蒸留留
去する濃縮工程、(9)濃縮した粗BHETをエステル
交換触媒とメタノール(MeOH)中でエステル交換反
応させ粗ジメチルテレフタレート(DMT)とEGを得
る工程、(10)液を冷却後、DMTケークとEG/M
eOH混合液とを分離する固液分離工程、(11)DM
TケークからMeOHを留出させ、DMTを精製する蒸
留工程、(12)回収精製DMTを溶融状態で保管し、
送液する工程、(13)回収精製DMTに対して重量比
で1:1〜1:4で水を投入し180℃で混合溶融保持
する工程、(14)混合溶融保持しているDMTと水を
送液し、230〜250℃で加水分解反応する工程、
(15)生成したテレフタル酸(TA)の水スラリーを
冷却する工程、(16)TAの水スラリーを遠心分離機
により脱水処理する工程、(17)含水TAを乾燥する
工程、(18)TA粉体を粉砕する工程、(19)TA
粉体を貯蔵する工程。」が提供される。Thus, according to the present invention, "a resin bottle waste containing polyethylene terephthalate (PET) as a main component and a component different from that,
A method for producing terephthalic acid from a resin bottle waste, which is sequentially provided in the following steps (1) to (19). (1) The step of unpacking the resin bottle waste packing bale containing the separated and collected PET as a main component and a different component, (2) the unpacked resin bottle waste is 2 to 30 mm Crushing process to make flakes of corners, (3) PET such as label thin film made of polyethylene (PE), polystyrene (PS), polyvinyl chloride (PVC), etc. from flaky resin bottle pieces
The process of separating the component polymers different from
(4) A decanter step that also serves to wash foreign substances inside and outside the resin bottle and / or the content residue inside the resin bottle with water and to separate the heterogeneous polymer such as PE or PP having a specific gravity smaller than that of water ( 5) A step of feeding the recovered PET flakes to the flakes storage tank by air feeding, and (6) charging the recovered PET flakes into ethylene glycol (EG) containing a PET depolymerization catalyst at a temperature of 175 ° C. to 190 ° C.
Treated under a pressure of 1 to 0.5 MPa, bis-β-
P to obtain hydroxyethyl terephthalate (BHET)
ET depolymerization step, (7) solid-liquid separation step of components not soluble in EG, (8) concentration step of distilling off EG components in crude BHET in the liquid, (9) transesterification catalyst of concentrated crude BHET To obtain crude dimethyl terephthalate (DMT) and EG by transesterification with methanol (MeOH), (10) after cooling the liquid, DMT cake and EG / M
solid-liquid separation step for separating the eOH mixture, (11) DM
A distillation step for distilling MeOH from the T-cake and purifying DMT, (12) storing the purified purified DMT in a molten state,
A step of sending a liquid, (13) a step of adding water in a weight ratio of 1: 1 to 1: 4 to the recovered and purified DMT, and mixing and holding the mixture at 180 ° C., (14) DMT and water which are held by mixing and melting And the step of carrying out a hydrolysis reaction at 230 to 250 ° C.,
(15) A step of cooling the generated water slurry of terephthalic acid (TA), (16) a step of dehydrating the TA water slurry by a centrifuge, (17) a step of drying the water-containing TA, (18) a TA powder Step of crushing the body, (19) TA
The step of storing powder. Is provided.
【0015】[0015]
【発明の実施の形態】以下、本発明の実施の形態につい
て詳細に説明する。本発明の製造方法においては、工程
(1)〜工程(5)までの、化学反応を伴う工程以前の
工程を前処理工程と呼ぶ。この前処理工程において、ポ
リエチレンテレフタレート(PET)を主成分として含
有しさらにそれとは異なる成分を含有する樹脂ボトル廃
棄物(例えば該回収PETボトル)を2〜30mm角の
フレーク状に粉砕する。該粉砕径はより好ましくは2〜
20mmである。該操作により解重合反応性が向上し、
PETボトル廃棄物の処理能力が向上する。この効果
は、ペットボトルの強度アップ及び寸法安定性のために
結晶化処理、白化させた部分の肉厚である箇所について
特に有効である。該粉砕物には、ボトルのキャップ又は
ラベルの材質であるポリエチレン、ポリプロピレン、ポ
リスチレン、ポリ塩化ビニル等のポリエステルとは異な
るポリマー類が混入する場合が多い。本発明では、これ
ら異ポリマー類の混入に対して、後の反応工程で分解し
て回収モノマーの純度を低下させることの無いような反
応条件を選択しているものの、該異ポリマー類は反応機
に付着する、フィルターの目詰まりを引き起こす等のハ
ンドリング上好ましくない影響を及ぼす可能性があるた
め、前処理工程において該異プラスチック類を除去し、
反応工程への混入を極力抑制することが反応を円滑に進
める上で重要となる。ただし、マテリアルリサイクルを
実施する場合のように該異ポリマー類を完全に除去する
ための多岐にわたる工程は必要とせず、必要最小限の工
程しか必要としない。BEST MODE FOR CARRYING OUT THE INVENTION Embodiments of the present invention will be described in detail below. In the manufacturing method of the present invention, the steps from step (1) to step (5) before the step involving the chemical reaction are referred to as the pretreatment step. In this pretreatment step, resin bottle waste (for example, the recovered PET bottle) containing polyethylene terephthalate (PET) as a main component and a component different from that is pulverized into flakes of 2 to 30 mm square. The crushed diameter is more preferably 2
It is 20 mm. The depolymerization reactivity is improved by the operation,
The processing capacity of PET bottle waste is improved. This effect is particularly effective for a portion having a wall thickness of a crystallized and whitened portion for increasing the strength and dimensional stability of the PET bottle. Polymers different from polyesters such as polyethylene, polypropylene, polystyrene and polyvinyl chloride, which are materials of bottle caps or labels, are often mixed in the pulverized products. In the present invention, the reaction conditions are selected such that the contamination of these foreign polymers does not degrade the purity of the recovered monomer by being decomposed in the subsequent reaction step. Adhered to the surface of the filter, it may have an unfavorable effect on handling such as clogging of the filter, so remove the foreign plastics in the pretreatment step,
It is important to suppress the mixture into the reaction process as much as possible for the reaction to proceed smoothly. However, it does not require a wide variety of steps for completely removing the different polymers as in the case of carrying out material recycling, and requires only the minimum necessary steps.
【0016】該粉砕したフレーク状の樹脂ボトル片か
ら、ポリエステルとは異なる、ラベル等に使用している
薄膜フィルム(ポリエチレン、ポリプロピレン、ポリ塩
化ビニル等)を除去するために、まず風力選別によりこ
れらを除去する。この際、あまり風量が大きいと有効成
分であるPETフレークスを同伴して除去することにな
ってしまうため、風量を適当に調節する必要がある。こ
の風力選別によりポリプロピレン、ポリスチレン、ポリ
塩化ビニルを主成分とするラベル等はほぼ完全に除去す
ることができる。In order to remove the thin film (polyethylene, polypropylene, polyvinyl chloride, etc.), which is different from polyester, used for labels, etc., from the crushed flaky resin bottle pieces, these are first subjected to air separation. Remove. At this time, if the air volume is too large, PET flakes, which is an active ingredient, will be removed together with it, so it is necessary to appropriately adjust the air volume. By this air force selection, a label containing polypropylene, polystyrene, or polyvinyl chloride as a main component can be almost completely removed.
【0017】次いで、風力選別では除去不可能なキャッ
プ等の異物を除去するため、風力選別されたフレークス
をデカンターに掛け、水よりも比重の軽いポリプロピレ
ン、ポリエチレン等の異ポリマー類を遠心分離法により
除去して回収PETフレークスを得る。該デカンター工
程は、ポリエステル樹脂ボトルに残留した食用などに由
来する不純物(醤油、清涼飲料等)を水洗することも兼ね
ているため、ボトル内に内容物が残留していても全く問
題が無い。遠心分離により分離された洗浄水は再度デカ
ンターへとリサイクルされ、一部はパージして排水処理
にかけられる。Next, in order to remove foreign matters such as caps which cannot be removed by air force selection, the wind-selected flakes are placed on a decanter, and different polymers such as polypropylene and polyethylene having a lower specific gravity than water are centrifuged. Remove to obtain recovered PET flakes. Since the decanter step also serves as washing the impurities (soy sauce, soft drink, etc.) derived from the edible residue remaining in the polyester resin bottle with water, there is no problem even if the contents remain in the bottle. The washing water separated by centrifugation is recycled again to the decanter, and a part of it is purged for wastewater treatment.
【0018】デカンターから排出された回収PETフレ
ークスは、空気輸送によって反応工程の反応機へと輸送
される。先の粉砕工程において粉砕後の大きさを30〜
150mmと比較的大きなものに規定した場合、この空
気輸送工程での輸送効率悪化、ロータリーバルブへの閉
塞等の問題点が生じるため、本発明においては2〜30
mmに粉砕することが大切である。なお、空気輸送前の
回収PETフレークスは、先のデカンター工程における
遠心分離の際に使用した水分が回収PETフレークスの
重量を基準として約0.5%残留している。これらの水
分は、継の解重合工程での反応速度に悪影響を及ぼすこ
とがあるが、空気輸送を行えば輸送中に乾燥され、最終
的には0.1%以下まで低下させることができるので、
反応進行上問題は無い。The recovered PET flakes discharged from the decanter are transported to the reactor in the reaction step by pneumatic transportation. In the previous crushing process, the size after crushing is 30 to
When it is specified to be relatively large as 150 mm, problems such as deterioration of transportation efficiency in this air transportation process and blockage of the rotary valve occur, so that in the present invention, 2 to 30.
It is important to grind to mm. In the recovered PET flakes before air transportation, about 0.5% of the water used during the centrifugal separation in the decanter process remains based on the weight of the recovered PET flakes. These waters may adversely affect the reaction rate in the successive depolymerization step, but if they are pneumatically transported, they are dried during transportation and can be finally reduced to 0.1% or less. ,
There is no problem in reaction progress.
【0019】以上の前処理工程で大部分のPET以外の
成分を除去することができ、マテリアルリサイクルを実
施する場合よりも大幅に少ない工程で前処理工程が完了
する。これは仮に少量の不純物が残留していたとして
も、次の反応工程で物理的・化学的な分離方法により該
不純物を分離することが可能であるためである。なお、
マテリアルリサイクルでは着色ボトルは不純物となり、
選別機によって除去されなければならないが、本発明に
おいては、着色ボトルに含まれる顔料も後の反応工程で
除去可能であるため、前処理工程での除去はあえて必要
とはしない。Most of the components other than PET can be removed by the above pretreatment process, and the pretreatment process can be completed in a significantly smaller number of steps than when material recycling is performed. This is because even if a small amount of impurities remain, the impurities can be separated by a physical / chemical separation method in the next reaction step. In addition,
In material recycling, colored bottles become impurities,
Although it has to be removed by a sorter, in the present invention, the pigment contained in the colored bottle can also be removed in the subsequent reaction step, and therefore the removal in the pretreatment step is not necessary.
【0020】次に、工程(6)において用いられる解重
合触媒としては、炭酸ナトリウム、カルボン酸のNa
塩、酢酸マンガン及び酢酸亜鉛の群から選ばれた少なく
とも1種の金属化合物を含み、かつその添加量が工程
(6)に供されるPETフレークス重量の0.1〜10
重量%の範囲とすることが好ましい。またこの工程
(6)で用いられるEGの量は、工程(6)に供される
PETフレークス重量の0.5〜20重量倍の範囲とす
ることが好ましい。なお、解重合反応の条件としては、
175〜190℃の温度、0.1〜0.5MPaの圧力
下とする。Next, as the depolymerization catalyst used in the step (6), sodium carbonate and carboxylic acid Na are used.
A salt containing at least one metal compound selected from the group consisting of manganese acetate and zinc acetate, and the addition amount thereof is 0.1 to 10 of the weight of PET flakes to be subjected to the step (6).
It is preferably in the range of wt%. The amount of EG used in step (6) is preferably in the range of 0.5 to 20 times the weight of PET flakes used in step (6). The conditions for the depolymerization reaction include:
The temperature is 175 to 190 ° C. and the pressure is 0.1 to 0.5 MPa.
【0021】工程(7)の固液分離工程では、上記解重
合反応後に、前処理工程で除去することができなかった
未溶解成分を分離除去する。工程(7)を通過した時点
でPETはビス−ω−ヒドロキシエチルテレフタレート
(BHET)に転化し、反応液はBHETとEGの混合
液(粗BHET)となっている。In the solid-liquid separation step of step (7), after the depolymerization reaction, undissolved components that could not be removed in the pretreatment step are separated and removed. When passing through the step (7), PET is converted into bis-ω-hydroxyethyl terephthalate (BHET), and the reaction liquid is a mixed liquid of BHET and EG (crude BHET).
【0022】工程(8)の濃縮工程においては、次工程
である工程(9)のエステル交換反応を効率的に進行さ
せるため、上記粗BHETから、好ましくはEGとPE
Tとの重量比率が原料仕込比基準で前者が後者の0.5
〜2.0倍になるまでEGを留去して、濃縮する。この
際の蒸留・濃縮操作は1.33kPa〜0.133MP
aの圧力下で行うことが好ましい。留去したEGは再度
工程(6)にリサイクルすることができる。In the concentration step of step (8), in order to efficiently proceed the transesterification reaction of step (9) which is the next step, from the above crude BHET, preferably EG and PE.
The weight ratio with T is based on the raw material charging ratio and the former is 0.5 of the latter.
Evaporate EG to ~ 2.0 times and concentrate. The distillation / concentration operation at this time is 1.33 kPa to 0.133 MP.
It is preferable to carry out under the pressure of a. The distilled EG can be recycled to the step (6) again.
【0023】工程(9)においては、上記工程(8)で
濃縮した粗BHETを、エステル交換触媒存在下でメタ
ノール(MeOH)とエステル交換反応させる。ここで
用いられるエステル交換反応触媒としては、炭酸ナトリ
ウム、カルボン酸のNa塩、酢酸マンガン及び酢酸亜鉛
の群から選ばれた少なくとも1種の金属化合物を含み、
かつその添加量が工程(6)に供されるPETフレーク
ス重量の0.1〜10重量%の範囲とすることが好まし
い。また、ここでで用いられるMeOHの量は、工程
(6)に供されるPETフレークス重量の0.5〜20
重量倍の範囲とすることすることが好ましい。反応条件
は、温度65〜85℃、圧力0.1〜0.3MPaの下
が好ましい。In the step (9), the crude BHET concentrated in the above step (8) is transesterified with methanol (MeOH) in the presence of a transesterification catalyst. The transesterification catalyst used here contains at least one metal compound selected from the group consisting of sodium carbonate, Na salt of carboxylic acid, manganese acetate and zinc acetate,
And, the addition amount thereof is preferably in the range of 0.1 to 10% by weight based on the weight of PET flakes used in the step (6). The amount of MeOH used here is 0.5 to 20 of the weight of PET flakes used in the step (6).
It is preferable to set the range to the weight times. The reaction conditions are preferably a temperature of 65 to 85 ° C. and a pressure of 0.1 to 0.3 MPa.
【0024】得られた反応生成物(DMT、EG、Me
OHの混合物)は冷却後、好ましくは遠心分離等の固液
分離手段により固液分離してDMTケーク(粗製DM
T)を得る。The reaction products obtained (DMT, EG, Me
After cooling the mixture of OH), solid-liquid separation is preferably carried out by solid-liquid separation means such as centrifugation to obtain a DMT cake (crude DM).
T) is obtained.
【0025】工程(11)においては、工程(10)で
得られたDMTケークから、蒸留により先ずMeOHを
留去させから蒸留精製して高純度の精製DMTを分離回
収する。回収精製DMTは溶融状態で保管し、必要に応
じて次工程の水及びDMT溶融混合工程に送液する。In step (11), the DMT cake obtained in step (10) is first distilled to remove MeOH and then purified by distillation to separate and collect highly purified DMT. The recovered and purified DMT is stored in a molten state and, if necessary, sent to the next step of water and DMT melt mixing step.
【0026】工程(13)において、回収精製DMTに
対して重量比で1:1〜1:4で水を投入し、170〜
190℃で攪拌下混合溶融保持する。In the step (13), water is added to the recovered and purified DMT at a weight ratio of 1: 1 to 1: 4, and 170-
Mix and hold under stirring at 190 ° C.
【0027】次に工程(14)において、工程(13)
から供されたDMTと水との溶融混合物を、バッチ式あ
るいは連続式の加水分解反応槽で温度230〜250
℃、圧力約2.8〜4MPaの加圧条件下、攪拌しなが
ら加水分解反応することが好ましい。この際、加水分解
反応により生じる主にメタノールからなる低沸点の反応
副生物は、反応槽頭部から反応水の蒸気と共に系外に排
出するのが好ましい。Next, in step (14), step (13)
The molten mixture of DMT and water provided by the above is heated in a batch or continuous hydrolysis reaction tank at a temperature of 230 to 250.
It is preferable to carry out the hydrolysis reaction while stirring under a pressure condition of ° C and a pressure of about 2.8 to 4 MPa. At this time, the low-boiling-point reaction by-product mainly composed of methanol generated by the hydrolysis reaction is preferably discharged from the reaction vessel head to the outside of the system together with the vapor of the reaction water.
【0028】工程(15)において上記反応性生物を冷
却して得たテレフタル酸(TA)の水スラリーは、工程
(16)の遠心分離機で脱水して、好ましくは含水率が
約10〜20%の含水TAケークとして分離回収する。The water slurry of terephthalic acid (TA) obtained by cooling the above reaction product in the step (15) is dehydrated in the centrifuge in the step (16), and preferably has a water content of about 10 to 20. Separated and collected as a water-containing TA cake of 100%.
【0029】得られた含水TAケークを、工程(17)
において、振動流動層式や不活性ガスの気流式乾燥機で
処理して、水分率0.5%以下のTA粉体を得る。さら
に工程(18)で、EGとの反応でPETポリマーをエ
ステル化から重縮合反応で得る際の反応性に影響のある
TAの粒径を調整するため、粉砕機で粉砕をおこなって
もよい。さらに工程(19)は、得られたTA紛体をP
ETポリマー製造施設へ払い出すための貯蔵工程であ
る。The obtained water-containing TA cake is subjected to the step (17).
In the above, the powder is treated with a vibratory fluidized bed type or an inert gas flow type dryer to obtain TA powder having a water content of 0.5% or less. Further, in the step (18), in order to adjust the particle size of TA which affects the reactivity when the PET polymer is obtained from the esterification through the polycondensation reaction by the reaction with EG, pulverization may be performed by a pulverizer. Further, in the step (19), the obtained TA powder is mixed with P
It is a storage process for delivering to the ET polymer manufacturing facility.
【0030】これらの工程を通過させることにより、D
MT及びモノメチルテレフタル酸(MMT)の総量がテ
レフタル酸に対して0.1〜1000ppmであり、さ
らには4−カルボキシベンズアルデヒド(4−CB
A)、パラトルイル酸(p−TA)、安息香酸(B
A)、ヒドロキシテレフタル酸ジメチル(HDT)の合
計の含有率が1ppm以下である高純度のテレフタル酸
を、樹脂ボトル廃棄物から効率よく回収することができ
る。このようなTAは、繊維、フィルム、PETボトル
などの樹脂用途に再利用することができ、特にボトル用
PETに適しているので、回収PETボトルを有効に再
活用することが可能となる。By passing through these steps, D
The total amount of MT and monomethyl terephthalic acid (MMT) is 0.1 to 1000 ppm with respect to terephthalic acid, and further 4-carboxybenzaldehyde (4-CB).
A), paratoluic acid (p-TA), benzoic acid (B
A) and high-purity terephthalic acid having a total content of dimethyl hydroxyterephthalate (HDT) of 1 ppm or less can be efficiently recovered from the waste of the resin bottle. Such TA can be reused for resin applications such as fibers, films, PET bottles and the like, and is particularly suitable for PET for bottles, so that the collected PET bottles can be effectively reused.
【0031】以下、本発明の樹脂ボトル廃棄物からのテ
レフタル酸製造プロセスの一態様を示す図1を用いて、
さらに具体的に説明する。Hereinafter, referring to FIG. 1, which shows one embodiment of the process for producing terephthalic acid from the waste resin bottle of the present invention,
A more specific description will be given.
【0032】工程(1)〜工程(5)の前処理工程(図
1に示さず。)により処理された回収PETフレークス
を供給源11から、また解重合触媒を供給槽10から、
さらにEGを供給ライン10aから、解重合槽1に同時
に仕込み、この解重合槽1中でPETフレークスを解重
合する。From the source 11, the recovered PET flakes treated by the pretreatment step (not shown in FIG. 1) of the steps (1) to (5), and the depolymerization catalyst from the supply tank 10,
Further, EG is simultaneously charged into the depolymerization tank 1 from the supply line 10a, and the PET flakes are depolymerized in the depolymerization tank 1.
【0033】解重合処理された混合物は固液分離装置2
に送られる。解重合槽1中で溶解しない成分は、固液分
離装置2中において分離され、固形物として系外に取り
除かれる。なお、この固形物は、更に洗浄槽3中におい
て、EGによって洗浄され、固形物表面の付着物は、必
要により解重合槽1に循環される。また固形物そのもの
は固形物槽16bへ分離除去される。ここで、解重合槽
1の滞留時間は1〜10時間、内温は175〜190℃
とすればよい。The depolymerized mixture is a solid-liquid separator 2
Sent to. Components that do not dissolve in the depolymerization tank 1 are separated in the solid-liquid separator 2 and removed outside the system as solids. The solid matter is further cleaned by EG in the cleaning tank 3, and the adhered matter on the surface of the solid matter is circulated to the depolymerization tank 1 if necessary. Further, the solid matter itself is separated and removed into the solid matter tank 16b. Here, the depolymerization tank 1 has a residence time of 1 to 10 hours and an internal temperature of 175 to 190 ° C.
And it is sufficient.
【0034】次いで、解重合反応が終了した解重合反応
物を、蒸留・濃縮槽4に送り、仕込み重量比でEGと解
重合反応物との比が0.5〜2となるようにEGを蒸留
・留去する。留去されたEGは、解重合槽1に循環供給
することができる。Next, the depolymerization reaction product after the depolymerization reaction is sent to the distillation / concentration tank 4, and EG is added so that the ratio of the weight ratio of EG to the depolymerization reaction product is 0.5 to 2. Distill and evaporate. The distilled EG can be circulated and supplied to the depolymerization tank 1.
【0035】次いで、濃縮した解重合反応物液をエステ
ル交換反応槽5に供給し、これにエステル交換反応触媒
をその供給源13から、またMeOHをその供給源12
から供給することによって、解重合反応物液をDMTと
EGに転換する。この時の、エステル交換反応槽内温
は、65〜85℃、0.1〜0.3MPaの内圧で滞留
時間を0.5〜5時間処理することが好ましい。Next, the concentrated depolymerization reaction product liquid is supplied to the transesterification reaction tank 5, to which the transesterification reaction catalyst is supplied, and MeOH is supplied from the supply source 12.
The depolymerization reaction product liquid is converted into DMT and EG by supplying from the above. At this time, it is preferable that the temperature in the transesterification reaction tank is treated at 65 to 85 ° C. and an internal pressure of 0.1 to 0.3 MPa for a residence time of 0.5 to 5 hours.
【0036】生成したDMTとEGとの混合物を、過剰
のMeOHとともに冷却し、これを固液分離装置6に供
給し、DMTのケークとEG及びMeOHの混合液とに
分離する。ここで、分離されたDMTのケークは、母液
としてEGを含液しているので、再度MeOHでスラリ
ー化して再度固液分離する。The produced mixture of DMT and EG is cooled together with excess MeOH, and this is supplied to the solid-liquid separator 6 to separate it into a cake of DMT and a mixture of EG and MeOH. Here, since the separated DMT cake contains EG as the mother liquor, it is again slurried with MeOH and solid-liquid separated again.
【0037】次いで、このDMTのケークをDMT蒸留
塔7に供給し、精製したDMTをDMT回収槽14に回
収する。この蒸留塔7の塔底の残液は、その一部をライ
ン7aを通して解重合槽1に戻し、残りを系外18に廃
棄する。Next, the cake of DMT is supplied to the DMT distillation column 7, and the purified DMT is recovered in the DMT recovery tank 14. A part of the residual liquid at the bottom of the distillation column 7 is returned to the depolymerization tank 1 through the line 7a, and the rest is discarded outside the system 18.
【0038】一方、固液分離装置6において分離された
EGとMeOHの混合液を、MeOH蒸留塔9及びEG
蒸留塔8に供給して、MeOH及びEGを留去する。こ
の留去MeOHはエステル交換反応槽5に供給するMe
OHの一部として使用することができる。さらに、Me
OH蒸留塔9塔底の残液をEG蒸留塔8に供給し、EG
を留去する。留去したEGの一部は、ライン10aを介
して解重合槽1に供給するEGとして使用し、残ったE
Gは回収して系外15に取り出す。なお、EG蒸留塔8
の残液の一部は解重合槽1に戻し、残りは廃棄物として
系外17に抜出す。On the other hand, the mixed liquid of EG and MeOH separated in the solid-liquid separation device 6 is supplied to the MeOH distillation column 9 and EG.
Supply to the distillation column 8 to distill off MeOH and EG. The distilled MeOH is supplied to the transesterification reaction tank 5 as Me.
It can be used as part of OH. Furthermore, Me
The residual liquid at the bottom of the OH distillation column 9 is supplied to the EG distillation column 8 to
Distill off. Part of the distilled EG was used as EG supplied to the depolymerization tank 1 via the line 10a, and the remaining E
G is collected and taken out of the system 15. The EG distillation tower 8
Part of the residual liquid of (1) is returned to the depolymerization tank 1, and the rest is discharged as waste to the outside of the system 17.
【0039】引き続いてDMTを加水分解反応してTA
を得る工程を図1で説明する。回収DMT槽14に蓄え
られた精製DMTは、溶融状態のまま、水供給ラインに
あるヒーター26で加熱された水ともに混合槽19へ送
液される。混合槽19内のDMT:水の重量比は1:1
〜1:4の範囲とし、好ましくは1:2〜1:3の範囲
とする。Subsequently, DMT is hydrolyzed to give TA.
The process of obtaining the above will be described with reference to FIG. The purified DMT stored in the recovery DMT tank 14 is sent to the mixing tank 19 together with the water heated by the heater 26 in the water supply line in the molten state. The weight ratio of DMT: water in the mixing tank 19 is 1: 1.
To 1: 4, preferably 1: 2 to 1: 3.
【0040】次いで、混合槽19からDMTと水の混合
液が第1加水分解反応槽20へ供給される。第1加水分
解反応槽20での反応温度は230〜250℃であるこ
と、特に240℃以上であることがより好ましく、その
際の反応圧力は約30〜40Kg/cm2(ゲージ圧)
である。反応槽上部から、加水分解反応で生成するMe
OHと過剰の水を所定反応分留去する際に、反応温度を
保持する場合に第1加水分解反応槽20にかかる圧力と
なる。滞留時間は1〜5時間であることが好ましい。Next, the mixed solution of DMT and water is supplied from the mixing tank 19 to the first hydrolysis reaction tank 20. The reaction temperature in the first hydrolysis reaction tank 20 is preferably 230 to 250 ° C., more preferably 240 ° C. or higher, and the reaction pressure at that time is about 30 to 40 kg / cm 2 (gauge pressure).
Is. Me generated in the hydrolysis reaction from the upper part of the reaction tank
The pressure is applied to the first hydrolysis reaction tank 20 when the reaction temperature is maintained when OH and excess water are distilled off by a predetermined reaction. The residence time is preferably 1 to 5 hours.
【0041】次いで第1加水分解反応槽20で生成した
TAと残留水及び未反応DMT、さらにDMTからTA
への反応中間体であるテレフタル酸モノメチル(MM
T)の混合水スラリーを第2加水分解反応槽21に供給
する。第2加水分解反応槽21での反応条件も第1加水
分解反応槽20と同様である。ただし、通常は第2加水
分解反応槽はDMTからTAへの加水分解反応が90%
以上進んだ状態からほぼ100%に近い反応転化率を達
成するために設ける。Next, TA generated in the first hydrolysis reaction tank 20, residual water and unreacted DMT, and TA from DMT
Monomethyl terephthalate (MM
The mixed water slurry of T) is supplied to the second hydrolysis reaction tank 21. The reaction conditions in the second hydrolysis reaction tank 21 are the same as those in the first hydrolysis reaction tank 20. However, 90% of the hydrolysis reaction from DMT to TA is usually carried out in the second hydrolysis reaction tank.
It is provided to achieve a reaction conversion rate close to 100% from the advanced state.
【0042】次に第2加水分解反応槽21で得られた高
温のTA/水スラリーを冷却するための冷却槽22へ供
給する。冷却されたTA/水スラリーを冷却槽22から
遠心分離機23に供給し、遠心分離された含水TAケー
クと水母液に分離する。Next, the high temperature TA / water slurry obtained in the second hydrolysis reaction tank 21 is supplied to a cooling tank 22 for cooling. The cooled TA / water slurry is supplied from the cooling tank 22 to the centrifuge 23, and separated into a centrifugal water-containing TA cake and a water mother liquor.
【0043】遠心分離機23で得られた含水TAケーク
は通常約10〜20%の水分率であり、乾燥機24で乾
燥してTA中の水分率を0.5%以下とする。この乾燥
後の粉体TAを必要に応じて25の粉砕造粒機で粒径調
整する。製品TA紛体はサイロ33に貯蔵し、PET化
工程へ供給する。The water-containing TA cake obtained by the centrifuge 23 usually has a moisture content of about 10 to 20%, and is dried by the dryer 24 to reduce the moisture content in TA to 0.5% or less. The particle size of the powder TA after drying is adjusted by a pulverizer / granulator 25 if necessary. The product TA powder is stored in the silo 33 and supplied to the PET process.
【0044】ここで、第1加水分解反応槽20から発生
する水/MeOH混合液はMeOH槽28に貯えられた
後、MeOH蒸留塔27でMeOHと水に蒸留分離さ
れ、MeOHは先のMeOH蒸留塔9に供給され再度蒸
留処理される。また、発生する水は廃棄処理される。ま
た、第2加水分解反応槽21で生成する水/MeOH混
合液は水26で加熱され、混合槽19へ再度循環供給さ
れる。Here, the water / MeOH mixed liquid generated from the first hydrolysis reaction tank 20 is stored in the MeOH tank 28 and then distilled and separated into MeOH and water in the MeOH distillation column 27, and the MeOH is distilled in the previous MeOH distillation. It is supplied to the column 9 and subjected to distillation again. In addition, the generated water is disposed of. Further, the water / MeOH mixed liquid generated in the second hydrolysis reaction tank 21 is heated with water 26 and is circulated and supplied again to the mixing tank 19.
【0045】また、遠心分離機23の母液である水は濾
液槽31に貯えられた後、濾過器30で水と遠心分離機
から母液側に含まれていたTAに濾別する。水は水槽2
9へ送られ、水ヒーター26経由混合槽19へ供給され
るか、排水処理される。Water, which is the mother liquor of the centrifuge 23, is stored in the filtrate tank 31 and is then filtered by the filter 30 into water and TA contained in the mother liquor from the centrifuge. Water is aquarium 2
9 is supplied to the mixing tank 19 via the water heater 26 or is treated for drainage.
【0046】[0046]
【実施例】以下実施例により本発明を更に具体的に説明
する。なお、実施例中の各値は種々の方法で測定できる
が、ここでは以下の方法に従って求めた。
4−カルボキシベンズアルデヒド(4−CBA)重量濃
度:得られたテレフタル酸を2N−アンモニア水に溶解
後、島津製液体クロマトグラフシステム(LC−6
A)、STRφDS−Hカラムで分離測定。
パラトルイル酸(p−TA)重量濃度:4−CBAと同
様。
ヒドロキシテレフタル酸ジメチル(HDT)重量濃度:
4−CBAと同様。
テレフタル酸ジメチル(DMT)重量濃度:高速液体ク
ロマトグラフィー(装置:日立社製HPLC D−70
00、充填式カラム:RP−18;2本)による。
テレフタル酸モノメチル(MMT)重量濃度:DMTと
同様
安息香酸(BA)濃度:ジアゾメタンでエステル化後、
n−トリデカンを内部標準として、10%SE−30を
分離カラムに用いたガスクロマトグラフで定量する。
テレフタル酸の250℃耐熱アルカリ透過性:テレフタ
ル酸を250℃で2時間処理した後、2N−KOHで溶
解後、400nmのUV透過率を分光光度計(日本分光
UVIDEC660相当)で測定する。テレフタル酸よ
り得られたPETポリマーの色相に与える影響の目安と
なる。The present invention will be described in more detail with reference to the following examples. Each value in the examples can be measured by various methods, but here, it was determined according to the following method. 4-Carboxybenzaldehyde (4-CBA) weight concentration: After dissolving the obtained terephthalic acid in 2N-ammonia water, Shimadzu liquid chromatograph system (LC-6)
A), separated measurement with STRφDS-H column. Paratoluic acid (p-TA) weight concentration: same as 4-CBA. Dimethyl hydroxyterephthalate (HDT) Weight concentration:
Same as 4-CBA. Dimethyl terephthalate (DMT) Weight concentration: High performance liquid chromatography (apparatus: Hitachi HPLC D-70)
00, packed column: RP-18; 2). Monomethyl terephthalate (MMT) Weight concentration: similar to DMT Benzoic acid (BA) concentration: After esterification with diazomethane,
Using n-tridecane as an internal standard, 10% SE-30 is used for the separation column for quantification by gas chromatography. 250 ° C heat-resistant alkali permeability of terephthalic acid: After terephthalic acid is treated at 250 ° C for 2 hours and dissolved in 2N-KOH, UV transmittance at 400 nm is measured with a spectrophotometer (equivalent to JASCO UVIDEC660). It is a measure of the influence on the hue of the PET polymer obtained from terephthalic acid.
【0047】[実施例1]分別収集・回収されたペット
ボトルベール(ベール寸法:900mm×1000mm
×550mmの120kgベール)を解梱包した後に粉
砕機に投入して粉砕機のスクリーン径を10mmに設定
して粉砕を行った。その後該粉砕物を風力選別機にか
け、ポリエチレン、ポリスチレン、ポリプロピレンを主
成分とするボトルに付属したラベルを除去した後、デカ
ンターによって遠心分離を行い、ボトルの内容物を水洗
・除去しつつポリプロプレン、ポリエチレンを主成分と
するキャップおよび風力選別で除去されなかったラベル
を除去し、回収PETフレークスとした。該回収PET
フレークスを空気輸送にて回収PETフレークス供給槽
へ貯蔵するため輸送した。次に回収PETフレークス供
給槽から100重量部の回収PETフレークス、EG供
給ラインからEGを360重量部、更に重合触媒供給槽
から炭酸ナトリウム2.7重量部を解重合槽へ供給し、
攪拌下、180℃で4時間半保持した。[Example 1] Separately collected and collected PET bottle veils (veil size: 900 mm x 1000 mm)
After unpacking (120 kg bale of x550 mm), it was put into a crusher and crushed by setting the screen diameter of the crusher to 10 mm. Then, the pulverized product is subjected to an air sorter, polyethylene, polystyrene, and after removing the label attached to the bottle containing polypropylene as the main component, centrifugation is performed by a decanter, while washing and removing the contents of the bottle with polypropylene, The cap containing polyethylene as a main component and the label that was not removed by the wind screening were removed to obtain recovered PET flakes. The collected PET
The flakes were transported by air transportation for storage in a recovered PET flakes supply tank. Next, 100 parts by weight of recovered PET flakes from the recovered PET flakes supply tank, 360 parts by weight of EG from the EG supply line, and 2.7 parts by weight of sodium carbonate from the polymerization catalyst supply tank were supplied to the depolymerization tank,
The mixture was kept under stirring at 180 ° C. for 4 hours and a half.
【0048】周囲を170℃に加熱している加熱器によ
って取り囲まれ、かつ、100メッシュ金網を濾材とし
て具備しているろ過装置に上記のEGによる解重合反応
処理液を投入して熱時ろ過を実施した。フィルター上の
残留物は170℃に加熱されたEG90重量部で洗浄
し、洗浄液は洗浄液受槽に貯えた。The above depolymerization reaction solution by EG is put into a filtration device which is surrounded by a heater which is heated to 170 ° C. and which is equipped with a 100-mesh wire mesh as a filter medium, to perform hot filtration. Carried out. The residue on the filter was washed with 90 parts by weight of EG heated to 170 ° C., and the washing liquid was stored in the washing liquid receiving tank.
【0049】熱時ろ過で得られた解重合反応処理液を
6.65kPaの減圧蒸留によって濃縮し、留分として
EG270重量部を回収した。The depolymerization reaction solution obtained by hot filtration was concentrated by vacuum distillation at 6.65 kPa, and 270 parts by weight of EG was recovered as a fraction.
【0050】この濃縮液、エステル交換触媒槽から炭酸
ナトリウム2.7重量部、更にMeOH180重量部を
エステル交換反応槽に投入し、常圧で液温75℃、攪拌
下1時間保持し、エステル交換反応を実施した。生成し
たDMT、EGとMeOHの混合物を40℃まで冷却
し、引き続いた固液分離装置でDMTケークを得た。該
DMTケークをMeOH洗浄槽に一旦投入し、MeOH
180重量部を投入して40℃で攪拌洗浄し、再度遠心
分離装置で固液分離し、DMTケークを得た。得られた
DMTケークを再度MeOH洗浄槽に投入し、今度は1
60℃でDMTを溶融すると同時に残存するMeOHを
留去した。溶融DMTをDMT蒸留塔に仕込み、圧力
6.65kPaの減圧蒸留で留分としてDMTを留出さ
せ83重量部を回収DMTとして得ることができた。こ
のDMTをDMT回収槽へ送液した。なお、このプロセ
スにおいて、回収されたDMTは不純物としての4−カ
ルボキシベンズアルデヒド(4−CBA)、パラトルイ
ル酸(p−TA)、安息香酸(BA)、ヒドロキシテレ
フタル酸ジメチル(HDT)の合計が1ppm以下の高
純度DMTであった。This concentrated liquid, 2.7 parts by weight of sodium carbonate from the transesterification catalyst tank, and further 180 parts by weight of MeOH were charged into the transesterification reaction tank, and the liquid temperature was kept at 75 ° C. under normal pressure for 1 hour with stirring to conduct transesterification. The reaction was carried out. The produced mixture of DMT, EG and MeOH was cooled to 40 ° C., and a DMT cake was obtained by the subsequent solid-liquid separation device. Once the DMT cake was put into a MeOH cleaning tank,
180 parts by weight was added, the mixture was stirred and washed at 40 ° C., and solid-liquid separation was performed again by a centrifugal separator to obtain a DMT cake. The obtained DMT cake was put into the MeOH washing tank again, this time to 1
At the same time as melting DMT at 60 ° C., the residual MeOH was distilled off. Molten DMT was charged into a DMT distillation column, and DMT was distilled as a fraction by vacuum distillation under a pressure of 6.65 kPa, and 83 parts by weight could be obtained as recovered DMT. This DMT was sent to the DMT recovery tank. In this process, the total amount of 4-carboxybenzaldehyde (4-CBA), paratoluic acid (p-TA), benzoic acid (BA), and dimethyl hydroxyterephthalate (HDT) as impurities was 1 ppm or less. It was a high-purity DMT of.
【0051】次に、DMT回収槽から溶融状態のDMT
を100重量部/時間の速度で、また水槽から200重
量部/時間の速度で各々連続的に混合槽へ供給し、混合
槽では180℃でDMTと水を攪拌保持しながら、混合
液を300重量部/時間の速度で第1加水分解反応槽へ
供給した。第1加水分解反応槽の液温を250℃とし、
攪拌しながら2時間の滞留時間を確保して反応させ、加
水分解反応で生成するMeOHは槽頭部より水とともに
留出させた。留出速度はMeOHと水の混合液として、
約76重量部/時間であり、この時の内圧は約4MPa
であった。得られたTA、水、DMTの混合スラリーは
第2加水分解反応槽へ約224重量部/時間で供給し
た。第2加水分解反応槽の液温も250℃とし、攪拌し
ながら1時間の滞留時間を確保して反応させ、生成する
MeOHは槽頭部より水とともに留出させた。留出速度
は留出速度はMeOHと水の混合液として、約58重量
部/時間であり、この時の内圧は約4MPaであった。Next, the molten DMT is collected from the DMT recovery tank.
Is continuously supplied to the mixing tank at a rate of 100 parts by weight / hour and at a rate of 200 parts by weight / hour from the water tank. It was supplied to the first hydrolysis reaction tank at a rate of parts by weight / hour. The liquid temperature of the first hydrolysis reaction tank is set to 250 ° C.,
While stirring, a retention time of 2 hours was secured and the reaction was carried out, and MeOH produced by the hydrolysis reaction was distilled out together with water from the head of the tank. The distillation rate is as a mixture of MeOH and water,
About 76 parts by weight / hour, and the internal pressure at this time is about 4 MPa
Met. The obtained mixed slurry of TA, water and DMT was supplied to the second hydrolysis reaction tank at about 224 parts by weight / hour. The liquid temperature of the second hydrolysis reaction tank was also set to 250 ° C., a residence time of 1 hour was secured while stirring, and the reaction was carried out, and MeOH produced was distilled out together with water from the head of the tank. The distillation rate was about 58 parts by weight / hour as a mixed solution of MeOH and water, and the internal pressure at this time was about 4 MPa.
【0052】得られたTAの水スラリーは冷却槽へ約1
66重量部/時間の速度で送液した。この冷却槽でのス
ラリー中のTA/水重量比は約1/1の重量比である。
約250℃の高温のTA/水スラリーを冷却槽のベント
コンデンサー、冷却内管、冷却ジャケットで約70℃に
冷却して保持した。この冷却槽から166重量部/時間
の速度でTA/水スラリーを遠心分離機へ送液し、遠心
分離機により処理して、TAのケークを得た。この含水
TAケークのTA/水重量比は約83:12であり、こ
のケークを窒素気流式乾燥機へ約95重量部/時間の速
度でダンプ供給して乾燥処理した。乾燥されたTA粉体
の水分率は0.2%であった。このTA粉体は、連続式
造粒粉砕機で平均粒径150μmに粒径調整したあと、
TA貯槽へ送付した。The resulting water slurry of TA is about 1 in the cooling tank.
The liquid was sent at a rate of 66 parts by weight / hour. The TA / water weight ratio in the slurry in this cooling tank is about 1/1 weight ratio.
The high temperature TA / water slurry of about 250 ° C. was cooled to about 70 ° C. by the vent condenser of the cooling tank, the cooling inner tube, and the cooling jacket and held. The TA / water slurry was sent from the cooling tank to the centrifuge at a rate of 166 parts by weight / hour and treated by the centrifuge to obtain a TA cake. The water-containing TA cake had a TA / water weight ratio of about 83:12, and the cake was dump-supplied to the nitrogen stream dryer at a rate of about 95 parts by weight / hour for drying treatment. The moisture content of the dried TA powder was 0.2%. This TA powder was adjusted to a mean particle size of 150 μm with a continuous granulator and
I sent it to the TA storage tank.
【0053】得られたTA中のDMT、MMTの濃度は
各々500ppmと50ppmであり、250℃耐熱ア
ルカリ透過性も99%以上であり、ボトル用PETの原
料として好適なTAであった。The concentrations of DMT and MMT in the obtained TA were 500 ppm and 50 ppm, respectively, and the 250 ° C. heat-resistant alkali permeability was 99% or more, and TA was suitable as a raw material for PET for bottles.
【0054】[比較例1]ペットボトルベールを解梱包
した後に粉砕機に投入して粉砕機のスクリーン径を10
mmに設定して粉砕を行ったが、その後の該粉砕物を風
力選別機にかけないで、デカンターによる遠心分離も、
ボトルの内容物を水洗・除去もしないで、単に小片化し
たのみのフレークスを回収PETフレークスとして使用
した以外は実施例1と同様に実施した。回収されたDM
Tを実施例1と同様に分析したが、液体クロマトグラフ
ィー、ガスクロマトグラフィーでは数多くの同定が不可
能な不純物が検出され、ここで得られたDMTは高純度
DMTとは呼べないものであった。また、加水分解で得
られたTAの250℃耐熱アルカリ透過性も93%と悪
かった。[Comparative Example 1] The PET bottle veil was unpacked and then put into a crusher to adjust the screen diameter of the crusher to 10
Milling was performed by setting to mm, but the subsequent pulverized product was not subjected to an air separator, and centrifugal separation by a decanter was also performed.
The procedure of Example 1 was repeated, except that the contents of the bottle were not washed and removed, and the flakes that were simply fragmented were used as the recovered PET flakes. DM recovered
T was analyzed in the same manner as in Example 1, but many unidentifiable impurities were detected by liquid chromatography and gas chromatography, and the DMT obtained here could not be called high-purity DMT. . Further, the 250 ° C heat-resistant alkali permeability of TA obtained by hydrolysis was also poor at 93%.
【0055】[比較例2]DMT回収段階でDMT蒸留
を省略した以外は実施例1と同様に実施した。回収され
たDMTを実施例1と同様に分析したが、液体クロマト
グラフィー、ガスクロマトグラフィーでは数多くの同定
が不可能な不純物が検出され、ここで得られたDMTは
高純度DMTとは呼べないものであった。また、加水分
解で得られたTAの250℃耐熱アルカリ透過性も90
%と悪かった。[Comparative Example 2] The same procedure as in Example 1 was carried out except that DMT distillation was omitted in the DMT recovery step. The recovered DMT was analyzed in the same manner as in Example 1, but many unidentifiable impurities were detected by liquid chromatography and gas chromatography, and the DMT obtained here cannot be called high-purity DMT. Met. In addition, the hydrolysis resistance of TA obtained at 250 ° C. is 90% against alkali resistance.
It was bad with%.
【0056】[0056]
【発明の効果】本発明によれば、回収された使用済みP
ETボトル等の、PETを主成分として含有しさらにそ
れとは異なる成分を含有する樹脂ボトル廃棄物廃棄物か
ら、DMTを経由して高純度のテレフタル酸が効率よく
得られる。これにより、その嵩高さから廃棄物の中でも
特に注目され、社会問題化されつつあるPETボトルを
有効に循環使用することが可能となり、その工業的価値
は極めて大である。According to the present invention, the used P recovered is recovered.
High-purity terephthalic acid can be efficiently obtained via DMT from a resin bottle waste waste containing PET as a main component and a component different from PET, such as an ET bottle. This makes it possible to effectively circulate PET bottles, which have become particularly socially problematic due to their bulkiness and are becoming a social problem, and their industrial value is extremely large.
【図1】本発明を実施するために使用される装置の一例
を示す該略模式図である。FIG. 1 is a schematic diagram showing an example of an apparatus used for carrying out the present invention.
1 :解重合槽 2 :固液分離装置 3 :洗浄槽 4 :蒸留濃縮槽 5 :エステル交換反応槽 6 :固液分離装置 6a :MeOH洗浄槽 7 :DMT蒸留塔 8 :EG蒸留塔 9 :MeOH蒸留塔 10 :重合触媒供給槽 10a:EG供給ライン 11 :回収PETフレークス供給槽 12 :MeOH供給槽 13 :エステル交換反応触媒槽 14 :DMT回収槽 15 :EG排出槽 16a:洗浄液受槽 16b:固形物槽 17 :EG蒸留釜残処理槽 18 :DMT蒸留釜残処理槽 19 :混合槽 20 :第1加水分解反応槽 21 :第2加水分解反応槽 22 :冷却槽 23 :遠心分離機 24 :乾燥機 25 :粉砕造粒機 26 :水ヒーター 27 :MeOH蒸留塔 28 :MeOH槽 29 :水槽 30 :ろ過器 31 :濾液槽 32 :排水処理装置 33 :TAサイロ 1: Depolymerization tank 2: Solid-liquid separator 3: Cleaning tank 4: Distillation concentrator 5: Transesterification reaction tank 6: Solid-liquid separator 6a: MeOH cleaning tank 7: DMT distillation column 8: EG distillation column 9: MeOH distillation column 10: Polymerization catalyst supply tank 10a: EG supply line 11: Recovery PET flakes supply tank 12: MeOH supply tank 13: Transesterification catalyst tank 14: DMT recovery tank 15: EG discharge tank 16a: Cleaning liquid receiving tank 16b: Solid matter tank 17: EG distillation tank residual treatment tank 18: DMT distillation tank residual treatment tank 19: Mixing tank 20: First hydrolysis reaction tank 21: Second hydrolysis reaction tank 22: Cooling tank 23: Centrifuge 24: Dryer 25: Grinding granulator 26: Water heater 27: MeOH distillation column 28: MeOH tank 29: Aquarium 30: Filter 31: Filtrate tank 32: Wastewater treatment device 33: TA silo
───────────────────────────────────────────────────── フロントページの続き (51)Int.Cl.7 識別記号 FI テーマコート゛(参考) C08L 67:00 C08L 67:00 (72)発明者 中島 実 愛媛県松山市北吉田町77番地 帝人株式会 社松山事業所内 Fターム(参考) 4F301 AA25 BF09 BF12 BF27 BG21 CA09 CA23 CA72 CA73 4H006 AA02 AC46 BA02 BA32 BC10 BC31 BC34 BC35 BC40 BE60 BS30 4H039 CA60 CA66 CE10 ─────────────────────────────────────────────────── ─── Continuation of front page (51) Int.Cl. 7 Identification code FI theme code (reference) C08L 67:00 C08L 67:00 (72) Inventor Minoru Nakajima 77 Kitayoshida-cho, Matsuyama-shi, Ehime Teijin Stock Exchange F term in company Matsuyama office (reference) 4F301 AA25 BF09 BF12 BF27 BG21 CA09 CA23 CA72 CA73 4H006 AA02 AC46 BA02 BA32 BC10 BC31 BC34 BC35 BC40 BE60 BS30 4H039 CA60 CA66 CE10
Claims (7)
を主成分として含有しさらにそれとは異なる成分を含有
する樹脂ボトル廃棄物を、下記工程(1)〜(19)に
順次供することを特徴とする、樹脂ボトル廃棄物からの
テレフタル酸の製造方法。 (1)分別収集・回収されたPETを主成分として含有
しさらにそれとは異なる成分を含有する樹脂ボトル廃棄
物梱包ベールを解梱包する工程、(2)解梱包した樹脂
ボトル廃棄物を2〜30mm角のフレーク状にする粉砕
工程、(3)フレーク状の樹脂ボトル片からポリエチレ
ン(PE)、ポリスチレン(PS)、ポリ塩化ビニル
(PVC)等からなるラベル薄膜フィルムなどのPET
と異なる成分ポリマーを風力選別により分離する工程、
(4)樹脂ボトル内外の異物及び/又は樹脂ボトル内の
中身残渣を水により洗浄することと、水よりも比重の小
さいPE、PP等の異成分ポリマーを分離することを兼
ねたデカンター工程、(5)回収PETフレークスをフ
レークス保管槽へ送る空送工程、(6)回収PETフレ
ークスをPET解重合触媒を含むエチレングリコール
(EG)中に投入して175℃〜190℃の温度、0.
1〜0.5MPaの圧力下において処理し、ビス−β−
ヒドロキシエチルテレフタレート(BHET)を得るP
ET解重合工程、(7)EGに溶解しない成分の固液分
離工程、(8)液中の粗BHET中のEG成分を蒸留留
去する濃縮工程、(9)濃縮した粗BHETをエステル
交換触媒とメタノール(MeOH)中でエステル交換反
応させ粗ジメチルテレフタレート(DMT)とEGを得
る工程、(10)液を冷却後、DMTケークとEG/M
eOH混合液とを分離する固液分離工程、(11)DM
TケークからMeOHを留出させ、DMTを精製する蒸
留工程、(12)回収精製DMTを溶融状態で保管し、
送液する工程、(13)回収精製DMTに対して重量比
で1:1〜1:4で水を投入し180℃で混合溶融保持
する工程、(14)混合溶融保持しているDMTと水を
送液し、230〜250℃で加水分解反応する工程、
(15)生成したテレフタル酸(TA)の水スラリーを
冷却する工程、(16)TAの水スラリーを遠心分離機
により脱水処理する工程、(17)含水TAを乾燥する
工程、(18)TA粉体を粉砕する工程、(19)TA
粉体を貯蔵する工程。1. Polyethylene terephthalate (PET)
A method for producing terephthalic acid from a resin bottle waste, characterized in that a resin bottle waste containing, as a main component, and a component different from that is sequentially supplied to the following steps (1) to (19). (1) The step of unpacking the resin bottle waste packing bale containing the separated and collected and collected PET as the main component and a different component, (2) the unpacked resin bottle waste is 2 to 30 mm Crushing process to make flakes of corners, (3) PET such as label thin film made of polyethylene (PE), polystyrene (PS), polyvinyl chloride (PVC), etc. from flaky resin bottle pieces
The process of separating the component polymers different from
(4) A decanter step that also serves to wash foreign substances inside and outside the resin bottle and / or the content residue inside the resin bottle with water and to separate a heterogeneous polymer such as PE or PP having a specific gravity smaller than that of water ( 5) A step of feeding the recovered PET flakes to the flakes storage tank by air feeding, and (6) charging the recovered PET flakes into ethylene glycol (EG) containing a PET depolymerization catalyst at a temperature of 175 ° C. to 190 ° C.
Treated under a pressure of 1 to 0.5 MPa, bis-β-
P to obtain hydroxyethyl terephthalate (BHET)
ET depolymerization step, (7) solid-liquid separation step of components not soluble in EG, (8) concentration step of distilling off EG components in crude BHET in the liquid, (9) transesterification catalyst of concentrated crude BHET To obtain crude dimethyl terephthalate (DMT) and EG by transesterification with methanol (MeOH), (10) after cooling the liquid, DMT cake and EG / M
solid-liquid separation step for separating the eOH mixture, (11) DM
A distillation step for distilling MeOH from the T-cake and purifying DMT, (12) storing the purified purified DMT in a molten state,
A step of sending a liquid, (13) a step of adding water in a weight ratio of 1: 1 to 1: 4 to the recovered and purified DMT, and mixing and maintaining the mixture at 180 ° C .; And the step of carrying out a hydrolysis reaction at 230 to 250 ° C.,
(15) A step of cooling the produced water slurry of terephthalic acid (TA), (16) a step of dehydrating the TA water slurry with a centrifuge, (17) a step of drying the water-containing TA, (18) a TA powder Step of crushing the body, (19) TA
The step of storing powder.
媒が、炭酸ナトリウム、カルボン酸のNa塩、酢酸マン
ガン及び酢酸亜鉛の群から選ばれる少なくとも1種の触
媒である請求項1記載のテレフタル酸の製造方法。2. The terephthalic acid according to claim 1, wherein the depolymerization catalyst used in the step (6) is at least one catalyst selected from the group consisting of sodium carbonate, Na salt of carboxylic acid, manganese acetate and zinc acetate. Manufacturing method.
媒の添加量が、回収PETフレークス重量に対して0.
1〜10重量%である請求項1又は2記載のテレフタル
酸の製造方法。3. The addition amount of the depolymerization catalyst used in the step (6) is 0.1% with respect to the weight of the recovered PET flakes.
The method for producing terephthalic acid according to claim 1, which is 1 to 10% by weight.
交換反応触媒が、炭酸ナトリウム、カルボン酸のNa
塩、酢酸マンガン及び酢酸亜鉛の群から選ばれる少なく
とも1種の触媒である請求項1記載のテレフタル酸の製
造方法。4. The transesterification catalyst used in step (9) is sodium carbonate or Na of carboxylic acid.
The method for producing terephthalic acid according to claim 1, which is at least one catalyst selected from the group consisting of salts, manganese acetate, and zinc acetate.
交換反応触媒の添加量が回収PETフレークス重量に対
して0.1〜10重量%である請求項1又は4記載のテ
レフタル酸の製造方法。5. The method for producing terephthalic acid according to claim 1, wherein the amount of the transesterification reaction catalyst used in step (9) is 0.1 to 10% by weight based on the weight of the recovered PET flakes.
レフタル酸ジメチル及びテレフタル酸モノメチルの総
量)が1000ppm以下である請求項1記載のテレフ
タル酸の製造方法。6. The method for producing terephthalic acid according to claim 1, wherein the unreacted impurities (total amount of dimethyl terephthalate and monomethyl terephthalate) in the product terephthalic acid is 1000 ppm or less.
カルボキシベンズアルデヒド(4−CBA)、パラトル
イル酸(p−TA)、安息香酸(BA)及びヒドロキシ
テレフタル酸ジメチル(HDT)の合計の含有率が1p
pm以下である請求項1記載のテレフタル酸の製造方
法。7. An impurity in the product terephthalic acid, which is 4-
The total content of carboxybenzaldehyde (4-CBA), paratoluic acid (p-TA), benzoic acid (BA) and dimethyl hydroxyterephthalate (HDT) is 1p.
The method for producing terephthalic acid according to claim 1, which is pm or less.
Priority Applications (12)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP2001317884A JP2003128600A (en) | 2001-10-16 | 2001-10-16 | Method for producing terephthalic acid from waste bottle |
| DE2002622792 DE60222792T2 (en) | 2001-10-16 | 2002-10-16 | METHOD FOR RECYCLING PET BOTTLES |
| KR20047005464A KR100866819B1 (en) | 2001-10-16 | 2002-10-16 | Method for recycling pet bottle |
| MXPA04003380A MXPA04003380A (en) | 2001-10-16 | 2002-10-16 | Method for recycling pet bottle. |
| EP02801581A EP1437377B1 (en) | 2001-10-16 | 2002-10-16 | Method for recycling pet bottle |
| PCT/JP2002/010754 WO2003033581A1 (en) | 2001-10-16 | 2002-10-16 | Method for recycling pet bottle |
| CNB028205863A CN1273524C (en) | 2001-10-16 | 2002-10-16 | Recycling methods for PET bottles |
| US10/491,783 US7462649B2 (en) | 2001-10-16 | 2002-10-16 | Method for recycling pet bottle |
| AT02801581T ATE374794T1 (en) | 2001-10-16 | 2002-10-16 | METHOD FOR RECYCLING PET BOTTLES |
| TW91123850A TW591049B (en) | 2001-10-16 | 2002-10-16 | Method for recycling PET bottle |
| DK02801581T DK1437377T3 (en) | 2001-10-16 | 2002-10-16 | Process for recycling PET bottles |
| US11/882,941 US20070299150A1 (en) | 2001-10-16 | 2007-08-07 | Method for recycling pet bottle |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP2001317884A JP2003128600A (en) | 2001-10-16 | 2001-10-16 | Method for producing terephthalic acid from waste bottle |
Publications (1)
| Publication Number | Publication Date |
|---|---|
| JP2003128600A true JP2003128600A (en) | 2003-05-08 |
Family
ID=19135683
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP2001317884A Pending JP2003128600A (en) | 2001-10-16 | 2001-10-16 | Method for producing terephthalic acid from waste bottle |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JP2003128600A (en) |
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| KR20250039380A (en) | 2022-07-15 | 2025-03-20 | 오사카 가스 케미칼 가부시키가이샤 | Depolymerization of resins having fluorene skeletons, their products and uses |
| WO2025164051A1 (en) * | 2024-01-31 | 2025-08-07 | 三菱重工業株式会社 | Hydrolysis reaction system and control method |
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| US12522695B2 (en) | 2019-10-08 | 2026-01-13 | Eastman Chemical Company | Catalyst systems for crystallizable reactor grade resins with recycled content |
| JP2023543768A (en) * | 2021-07-19 | 2023-10-18 | エルジー・ケム・リミテッド | Monomer composition for synthesizing recycled plastics, method for producing the same, recycled plastics, molded products, and plasticizer compositions using the same |
| JP7531056B2 (en) | 2021-07-19 | 2024-08-08 | エルジー・ケム・リミテッド | Monomer composition for synthesizing recycled plastics, its manufacturing method, and recycled plastics, molded articles, and plasticizer compositions using the same |
| TWI865893B (en) * | 2021-07-19 | 2024-12-11 | 南韓商Lg化學股份有限公司 | Monomer composition for synthesizing recycled plastic, prepration method thereof, and recycled plastic, molded product, plasticizer composition using the same |
| KR20250039380A (en) | 2022-07-15 | 2025-03-20 | 오사카 가스 케미칼 가부시키가이샤 | Depolymerization of resins having fluorene skeletons, their products and uses |
| WO2025164051A1 (en) * | 2024-01-31 | 2025-08-07 | 三菱重工業株式会社 | Hydrolysis reaction system and control method |
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