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JP2005002161A - Method for removing different kind of plastic - Google Patents

Method for removing different kind of plastic Download PDF

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Publication number
JP2005002161A
JP2005002161A JP2003164818A JP2003164818A JP2005002161A JP 2005002161 A JP2005002161 A JP 2005002161A JP 2003164818 A JP2003164818 A JP 2003164818A JP 2003164818 A JP2003164818 A JP 2003164818A JP 2005002161 A JP2005002161 A JP 2005002161A
Authority
JP
Japan
Prior art keywords
depolymerization
liquid
plastic
polyester waste
polyalkylene terephthalate
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
Application number
JP2003164818A
Other languages
Japanese (ja)
Inventor
Koji Mukai
浩二 向井
Hiroshi Horiuchi
裕志 堀内
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Teijin Frontier Co Ltd
Original Assignee
Teijin Fibers Ltd
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Teijin Fibers Ltd filed Critical Teijin Fibers Ltd
Priority to JP2003164818A priority Critical patent/JP2005002161A/en
Publication of JP2005002161A publication Critical patent/JP2005002161A/en
Pending legal-status Critical Current

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Classifications

    • CCHEMISTRY; METALLURGY
    • C08ORGANIC MACROMOLECULAR COMPOUNDS; THEIR PREPARATION OR CHEMICAL WORKING-UP; COMPOSITIONS BASED THEREON
    • C08JWORKING-UP; GENERAL PROCESSES OF COMPOUNDING; AFTER-TREATMENT NOT COVERED BY SUBCLASSES C08B, C08C, C08F, C08G or C08H
    • C08J11/00Recovery or working-up of waste materials
    • C08J11/04Recovery or working-up of waste materials of polymers
    • C08J11/10Recovery or working-up of waste materials of polymers by chemically breaking down the molecular chains of polymers or breaking of crosslinks, e.g. devulcanisation
    • C08J11/18Recovery or working-up of waste materials of polymers by chemically breaking down the molecular chains of polymers or breaking of crosslinks, e.g. devulcanisation by treatment with organic material
    • C08J11/22Recovery or working-up of waste materials of polymers by chemically breaking down the molecular chains of polymers or breaking of crosslinks, e.g. devulcanisation by treatment with organic material by treatment with organic oxygen-containing compounds
    • C08J11/24Recovery or working-up of waste materials of polymers by chemically breaking down the molecular chains of polymers or breaking of crosslinks, e.g. devulcanisation by treatment with organic material by treatment with organic oxygen-containing compounds containing hydroxyl groups
    • CCHEMISTRY; METALLURGY
    • C08ORGANIC MACROMOLECULAR COMPOUNDS; THEIR PREPARATION OR CHEMICAL WORKING-UP; COMPOSITIONS BASED THEREON
    • C08JWORKING-UP; GENERAL PROCESSES OF COMPOUNDING; AFTER-TREATMENT NOT COVERED BY SUBCLASSES C08B, C08C, C08F, C08G or C08H
    • C08J2367/00Characterised by the use of polyesters obtained by reactions forming a carboxylic ester link in the main chain; Derivatives of such polymers
    • C08J2367/02Polyesters derived from dicarboxylic acids and dihydroxy compounds
    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W30/00Technologies for solid waste management
    • Y02W30/50Reuse, recycling or recovery technologies
    • Y02W30/62Plastics recycling; Rubber recycling

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  • Chemical & Material Sciences (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Sustainable Development (AREA)
  • Health & Medical Sciences (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Medicinal Chemistry (AREA)
  • Polymers & Plastics (AREA)
  • Organic Chemistry (AREA)
  • Separation, Recovery Or Treatment Of Waste Materials Containing Plastics (AREA)

Abstract

<P>PROBLEM TO BE SOLVED: To provide a method for preventing troubles in a recycling process, in recovering an effective component from a polyester waste containing as the main component a polyalkylene terephthalate, by separating and removing a different kind of plastic contained in the polyester waste in a depolymerization reaction tank and omitting liquid-feeding to the next process. <P>SOLUTION: The method for removing the different kind of plastic from the polyester waste comprises removing the polyester waste, which is mainly composed of the polyalkylene terephthalate and contains the different kind of plastic from the polyalkylene terephthalate, where the polyester waste is successively subjected to the following steps (1) and (2): (1) a step for throwing the polyester waste into a depolymerization reaction step for depolymerization by a polyalkylene glycol to cause a part or the whole of the polyalkylene terephthalate to be depolymerized to obtain a depolymerization liquid; and (2) a step for drawing out the different kind of plastic which has a smaller specific gravity than the depolymerization liquid and floats in the vicinity of the liquid level of the depolymerization liquid while keeping the temperature of the depolymerization liquid within the range of 120-180°C at the time of removing the different kind of plastic in a solid state contained in the depolymerization liquid out of the system. <P>COPYRIGHT: (C)2005,JPO&NCIPI

Description

【0001】
【発明の属する技術分野】
本発明は、ポリエチレンテレフタレートを主成分として含有するポリエステル廃棄物から有効成分を回収する方法に関する。さらに詳しくは、ポリエステル廃棄物に含まれる異種プラスチックを解重合槽にて分離除去し、リサイクル工程内での工程トラブルを防止する方法に関する。
【0002】
【従来の技術】
ポリエチレンテレフタレートは、その化学的安定性が優れていることから、繊維、フイルム、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などでの使用が急速に増大している。
【0003】
しかしながら、上記のような使用量の増大に伴って大量に発生する使用済みポリエチレンテレフタレート(特に使用済みの飲料用ボトル)、およびポリエチレンテレフタレート製造段階で発生する品質不適格品(以下、これらを「ポリエステル廃棄物」と略称することがある。)の処理は、大きな社会問題となっている。
【0004】
上記の問題に対して、ポリエステル廃棄物をモノマーに変換・回収し、このモノマーを原料にして再度重合反応によってポリエチレンテレフタレートを製造し再利用する、いわゆるケミカルリサイクルが有効である。この方法は、基本的にロスの無い、化合物の循環再使用が可能であり、資源の再利用が可能となる。
【0005】
すなわち、これら回収したポリエステル廃棄物はエチレングリコールで解重合反応し、次いでメタノールを用いてエステル交換反応を行い、更に分離精製することでテレフタル酸ジメチルおよびエチレングリコールとして回収され、資源の有効利用、トータルコストの低下につながる。
【0006】
例えば、ポリエチレンテレフタレートにエチレングリコールを過剰に加えて加熱し、解重合反応によりビス(β−ヒドロキシエチル)テレフタレート及び末端にβ−ヒドロキシエチルエステル基を含む低重合体の混合物を得、該混合物に対し過剰のメタノールを加え触媒の存在下、置換エステル化反応することによりテレフタル酸ジメチルを回収する方法が記載されている(例えば特許文献1参照。)。
【0007】
しかし、ケミカルリサイクルによってポリエステル廃棄物を処理する場合、ポリエステル廃棄物、特に飲料用ボトルに含まれる異物を取り除くことが重要となる。従来、飲料用ボトルに含まれるキャップやラベル等の異物は、手作業や水を用いた比重分離により除去されていたが、手作業であれば大量処理が困難でありまた経済的に好ましくなく、水を用いた比重分離方法では、水より比重の大きな物質は実質上分離不可能である。
【0008】
一方、該異物の完全な除去ができないとリサイクル工程内に異物が混入することとなり、異物は固形或いは高温条件で一部溶融することにより、リサイクル工程内の機器への付着や配管の閉塞などのトラブルが発生する。
【0009】
また、ポリエステル廃棄物からテレフタル酸ジメチル及びエチレングリコールを分離回収する方法を提案されている(例えば特許文献2参照)。その特許文献では、異物成分を含むポリエステル廃棄物をアルキレングリコールにより解重合し、次いでメタノールでエステル交換反応することでテレフタル酸ジメチルとエチレングリコールを回収する方法を提案されている。更に、該特許文献中に、得られた解重合反応液中に含まれる固形異物のうち、この溶液の表面に浮遊している固形異物分、例えば、ポリオレフィンを、浮遊選別により除去する方法が提案されている。本発明者らは特許文献2のように異物除去方法を提案しているが、それでもなお該方法を用いても表面に浮遊している異物を除去する際、および溶液と異物とを分離する際に異物が装置や配管等に付着、閉塞させるなどの課題が残っていた。
【0010】
【特許文献1】
特公昭43−2088号公報
【0011】
【特許文献2】
国際公開第01/30729号パンフレット
【0012】
【発明が解決しようとする課題】
本発明の目的は、上記従来技術が有していた問題点を解消し、ポリエステル廃棄物中に含まれる異種プラスチックを解重合槽にて分離除去する際に、次工程への送りをなくしケミカルリサイクル工程内でのトラブルを防止する方法を提供することにある。
【0013】
【課題を解決するための手段】
本発明者らは上記従来技術に鑑み、鋭意検討を行った結果、本発明を完成するに至った。すなわち本発明は、
ポリアルキレンテレフタレートを主成分とし、ポリアルキレンテレフタレートとは異種のプラスチックを含むポリエステル廃棄物から異種プラスチックを除去する方法であって、下記(1)、(2)の各工程を逐次的に通過させることを特徴とする異種プラスチック除去方法である。
(1)アルキレングリコールにより解重合反応させる解重合反応工程へ投入し、該ポリアルキレンテレフタレートの一部または全部を解重合反応させて解重合液とする工程。
(2)該解重合液中に含まれる固体の異種プラスチックを系外へ除去する際に、該解重合液温度を120℃〜180℃の範囲に制御しつつ、該解重合液の液面近傍に浮遊する該解重合液よりも比重の小さな異種プラスチックを抜き出す工程。
【0014】
なお、この発明の中で解重合液温度を130℃〜170℃の範囲に制御する除去方法、アルキレングリコールがエチレングリコールである除去方法、ポリエステル廃棄物中に主成分として含まれるポリアルキレンテレフタレートがポリエチレンテレフタレートである除去方法、ポリエチレンテレフタレートが回収したPETボトル由来である除去方法が好ましい。
【0015】
【発明の実施の形態】
以下に、本発明の実施の形態を、実施例などを使用して説明する。なお、これらの実施例など及び説明は本発明を例示するものであり、本発明の範囲を制限するものではない。本発明の趣旨に合致する限り他の実施形態も本発明の範疇に属し得ることは言うまでもない。
【0016】
本発明の除去方法において、ポリアルキレンテレフタレートとはテレフタル酸もしくはその誘導体とアルキレングリコールから当業者が通常の製造方法で得ることができるポリアルキレンテレフタレートを指す。また「ポリアルキレンテレフタレートを主成分とし」とは後述のポリエステル廃棄物中、80重量%以上がポリアルキレンテレフタレートであることを示す。またポリエステル廃棄物中のポリエステルとはポリエチレンテレフタレート、ポリトリメチレンテレフタレート、ポリブチレンテレフタレートなどがあげられるが市場の流通及び経済性の面よりポリエチレンテレフタレートが多く使用されておりかつ好ましく用いられる。更に本発明の除去方法においては、下記の二つの工程を逐次的に通過させ達成することが出来る。
【0017】
すなわち第一の工程はアルキレングリコールによりポリエステル廃棄物を解重合反応させる解重合工程へ投入し、ポリアルキレングリコールの一部または全部を解重合反応させて解重合液とする工程である。ポリエステル廃棄物は一般に水洗浄及び粗粉砕などの前処理を施し、解重合反応に適した形状にしてから解重合反応槽に投入することが好ましい。本発明の除去方法は、連続又は回分方式のいずれにも適用できる。回分方式で実施する場合においては、前記ポリエステル廃棄物を、ポリエステル解重合触媒を含むアルキレングリコールが主成分の溶液中、解重合反応させ、解重合液とする。その解重合触媒としては、アルカリ金属の炭酸塩、水酸化物、若しくは酢酸塩、アルカリ土類金属の炭酸塩、水酸化物、若しくは酢酸塩、またはマンガン、若しくは亜鉛の酢酸塩よりなる群から少なくとも1種選ばれる化合物を用いるのが好ましい。またこの際用いるアルキレングリコールとしてエチレングリコールを用いるのが好ましい。該解重合反応槽には、反応を促進させるために攪拌機や解重合反応槽の自己循環ライン等設置し、アルキレングリコール若しくは解重合液を循環しながら解重合を進めることが好ましい。
【0018】
この解重合反応時、ポリエステル廃棄物に含まれる異種プラスチックのうち、解重合液に対して比重の小さいポリエチレン、ポリプロピレン、ポリスチレン等のポリオレフィンを主成分としたプラスチックは解重合液の液面近傍に浮遊する。通常、解重合液に対して比重がかなり小さい異種プラスチックは、目視で容易に区別できる程度に解重合液の液面にまで上昇し浮遊するが、比重の差がごく小さい場合はそれほどまで明確に浮遊しているとは言えない場合もある。また液面の面積に対して異種プラスチックの量が多い場合は、狭い液面に対して異種プラスチックが込み合った状態で浮遊することがある。このような場合には、液面に浮遊している異種プラスチックを取り除けば液面まで上昇し浮遊するが、液面にある異種プラスチックがあるために、結果として液面まで上昇できないこともありうる。「液面近傍に浮遊する」とはこれら等の原因で、結果として液面で浮遊していない異種プラスチックを取り除くことも本発明に含めるものである。
【0019】
これらの浮遊した異種プラスチックは、上層部の解重合液と同時に抜出すことにより除去を行う。この除去工程については、ポリアルキレンテレフタレートの解重合反応が完全に終了していない段階でも、異種プラスチックが充分に分離できるほど浮遊し、或いは未反応のポリアルキレンテレフタレートが残存したスラリー状態であっても実施可能である。すなわちポリアルキレンテレフタレートのうち全部が解重合反応している状態でも、または一部が解重合反応している状態で実施可能である。
【0020】
次の第二の工程は該解重合液中に含まれる固体の異種プラスチックを系外へ除去する際に、外界重合液温度を120〜180℃の範囲に制御しつつ、外解重合液の表面近傍に浮遊する該解重合液よりも比重の小さな異種プラスチックを抜き出す工程である。解重合反応槽から解重合液と異物を分離する場合には、解重合液温度を120〜180℃に保っておく必要がある。180℃を超える場合は異種プラスチックの粘性が増すことから、融着を起こし解重合反応槽からの浮遊物抜出しが困難となる。好ましくは解重合液温度を130℃〜170℃の範囲に制御することである。この温度範囲を保つとポリオレフィンを主成分とした異種プラスチックの粘性を落とし、異種プラスチックを硬化させたまま解重合液の粘性を落とさない状態を保つことができ、異種プラスチックの次工程への送りをなくし次工程以降でのトラブルを防止することが可能である。また解重合液を次工程へ送る際にも、この温度を保っておくことが送液を容易にすることが出来る点で好ましい。また、解重合反応槽では、一般的に反応を促進させるため攪拌機や循環ポンプなどを用いて解重合反応槽内の液を循環させることが好ましい。
【0021】
また、該解重合反応槽では、解重合反応を必ずしも完全に実施する必要はなく、このため、取り出し時ポリアルキレンテレフタレートの未反応分が残存している状態でも適用できる。更には、解重合反応がある一定以上進行した状態であれば、解重合反応槽から次工程へ送液する箇所の濾過やストレーナーなどの装置を設置することも可能である。
【0022】
【実施例】
以下実施例により本発明の内容を更に具体的に説明するが本発明はこれにより何等限定を受けるものではない。なお、実施例中の各値は以下の方法に従って求めた。
【0023】
[実施例1]
ポリエチレンテレフタレート50部、ポリスチレン2部、ポリエチレン2部、エチレングリコール200部と解重合触媒として炭酸ナトリウム1.5部を解反応重合槽に投入し、100rpmで攪拌下170℃に昇温した。そのままの状態で1時間保持した。この時点で投入したポリエチレンテレフタレートの一部は反応し、未反応物は解重合液中に浮遊した状態であり、ポリスチレン及びポリエチレンは解重合液面に小さな粒上で浮遊した。この状態で攪拌を一度停止し、液面に近い上部の解重合液をポリスチレン及びポリエチレンとともに20部抜き出したところは、ポリスチレン及びポリエチレンが3.8部抜き出され、解重合槽に残った液中にはポリエチレン及びポリスチレンが0.2部のみ残存した。またポリエチレンもしくはポリスチレンが配管へ付着する、配管が閉塞を起こすといった問題も起こらなかった。
【0024】
[比較例1]
ポリエチレンテレフタレート50部、ポリスチレン2部、ポリエチレン2部、エチレングリコール200部と解重合触媒として炭酸ナトリウム1.5部を解反応重合槽に投入し、100rpmで攪拌下185℃に昇温した。さらにそのままの状態で100rpmで攪拌下4時間保持したところ、ポリエチレンテレフタレートは溶解し解重合反応が完結した。この時点で、投入したポリスチレン及びポリエチレンは解重合液面に浮遊したが粘性がますことから融着し大きな塊状となった。この状態で攪拌を一度停止し、液面に近い上部の解重合液をポリスチレン及びポリエチレンとともに20部抜き出したところは、ポリスチレン及びポリエチレンが完全に抜き出しできず、解反応重合槽に残った解重合液中に2部残存した。
【0025】
【発明の効果】
本発明の除去方法によれば、ポリエチレンテレフタレートを主成分として含有するポリエステル廃棄物から有効成分を回収する場合、ポリエステル廃棄物に含まれる比重の小さい異種プラスチックを解重合槽にて分離除去し、次工程への送りをなくし、リサイクル工程内での工程トラブルを防止することが可能である。
[0001]
BACKGROUND OF THE INVENTION
The present invention relates to a method for recovering an active ingredient from a polyester waste containing polyethylene terephthalate as a main component. More specifically, the present invention relates to a method for preventing a process trouble in a recycling process by separating and removing different plastics contained in polyester waste in a depolymerization tank.
[0002]
[Prior art]
Since polyethylene terephthalate is excellent in chemical stability, its use in food fields such as life-related materials such as fibers, films and resins, drinking water, bottles for carbonated beverages and the like is rapidly increasing.
[0003]
However, the used polyethylene terephthalate (especially used beverage bottles) generated in large quantities with the increase in the amount used as described above, and the quality inadequate products generated in the polyethylene terephthalate manufacturing stage (hereinafter referred to as “polyester”). The process of “waste” may be abbreviated as a big social problem.
[0004]
In order to solve the above problems, so-called chemical recycling is effective, in which polyester waste is converted and recovered into a monomer, and polyethylene terephthalate is produced and reused by a polymerization reaction using the monomer as a raw material. In this method, the compound can be recycled and reused without any loss, and resources can be reused.
[0005]
That is, these recovered polyester wastes are depolymerized with ethylene glycol, then transesterified with methanol, and further separated and purified to be recovered as dimethyl terephthalate and ethylene glycol for effective use of resources, total This leads to cost reduction.
[0006]
For example, an excessive amount of ethylene glycol is added to polyethylene terephthalate and heated, and a depolymerization reaction yields a mixture of bis (β-hydroxyethyl) terephthalate and a low polymer containing a β-hydroxyethyl ester group at the end. A method for recovering dimethyl terephthalate by adding an excess of methanol and carrying out a substitution esterification reaction in the presence of a catalyst is described (for example, see Patent Document 1).
[0007]
However, when polyester waste is processed by chemical recycling, it is important to remove foreign matters contained in the polyester waste, particularly beverage bottles. Conventionally, foreign substances such as caps and labels contained in beverage bottles have been removed by manual gravity or specific gravity separation using water, but if it is manual labor, mass processing is difficult and economically undesirable, In the specific gravity separation method using water, a substance having a specific gravity greater than that of water cannot be substantially separated.
[0008]
On the other hand, if the foreign matter cannot be completely removed, the foreign matter will be mixed in the recycling process, and the foreign matter may partially melt at a solid or high temperature condition, causing adhesion to equipment in the recycling process or blockage of piping. Trouble occurs.
[0009]
In addition, a method for separating and recovering dimethyl terephthalate and ethylene glycol from polyester waste has been proposed (see, for example, Patent Document 2). The patent document proposes a method of recovering dimethyl terephthalate and ethylene glycol by depolymerizing a polyester waste containing a foreign component with alkylene glycol and then transesterifying with methanol. Further, the patent document proposes a method of removing solid foreign matters floating on the surface of the solution, for example, polyolefin, by solid-state separation, among solid foreign matters contained in the obtained depolymerization reaction solution. Has been. The present inventors have proposed a foreign matter removal method as in Patent Document 2, but nevertheless, when removing the foreign matter floating on the surface even when the method is used, and when separating the solution from the foreign matter However, there are still problems such as foreign matter adhering to and blocking the device and piping.
[0010]
[Patent Document 1]
Japanese Patent Publication No. 43-2088 [0011]
[Patent Document 2]
International Publication No. 01/30729 Pamphlet [0012]
[Problems to be solved by the invention]
The object of the present invention is to eliminate the problems with the prior art described above, and eliminate the need to send to the next process when separating and removing different plastics contained in polyester waste in a depolymerization tank. The object is to provide a method for preventing troubles in the process.
[0013]
[Means for Solving the Problems]
As a result of intensive studies in view of the above-described prior art, the present inventors have completed the present invention. That is, the present invention
Polyalkylene terephthalate is a main component, and polyalkylene terephthalate is a method for removing different plastics from polyester waste containing different plastics, and sequentially passing the following steps (1) and (2). This is a method for removing different types of plastics.
(1) A step of putting into a depolymerization reaction step of depolymerizing with an alkylene glycol and depolymerizing a part or all of the polyalkylene terephthalate to obtain a depolymerization solution.
(2) When the solid different plastic contained in the depolymerization liquid is removed from the system, the temperature of the depolymerization liquid is controlled in the range of 120 ° C. to 180 ° C. A step of extracting a different kind of plastic having a specific gravity smaller than that of the depolymerization solution floating on the surface.
[0014]
In this invention, the removal method for controlling the temperature of the depolymerization solution in the range of 130 ° C. to 170 ° C., the removal method in which the alkylene glycol is ethylene glycol, and the polyalkylene terephthalate contained as a main component in the polyester waste is polyethylene. A removal method that is terephthalate and a removal method that is derived from a PET bottle recovered from polyethylene terephthalate are preferred.
[0015]
DETAILED DESCRIPTION OF THE INVENTION
Hereinafter, embodiments of the present invention will be described with reference to examples. In addition, these Examples etc. and description illustrate this invention, and do not restrict | limit the scope of the present invention. It goes without saying that other embodiments may belong to the category of the present invention as long as they match the gist of the present invention.
[0016]
In the removal method of the present invention, polyalkylene terephthalate refers to polyalkylene terephthalate that can be obtained from terephthalic acid or a derivative thereof and alkylene glycol by a usual production method. Further, “based on polyalkylene terephthalate” means that 80% by weight or more of the polyester waste described later is polyalkylene terephthalate. Polyester in the polyester waste includes polyethylene terephthalate, polytrimethylene terephthalate, polybutylene terephthalate and the like, but polyethylene terephthalate is often used and preferably used from the viewpoint of market distribution and economy. Furthermore, in the removal method of the present invention, the following two steps can be sequentially passed.
[0017]
That is, the first step is a step in which a polyester waste is depolymerized with alkylene glycol, and the polyalkylene glycol is partially or completely depolymerized to form a depolymerization solution. In general, it is preferable that polyester waste is pretreated such as washing with water and coarsely pulverized to have a shape suitable for the depolymerization reaction and then put into the depolymerization reaction tank. The removal method of the present invention can be applied to either a continuous or batch system. In the case of carrying out in a batch system, the polyester waste is subjected to a depolymerization reaction in a solution containing an alkylene glycol containing a polyester depolymerization catalyst as a main component to obtain a depolymerization solution. The depolymerization catalyst includes at least one selected from the group consisting of alkali metal carbonates, hydroxides or acetates, alkaline earth metal carbonates, hydroxides or acetates, or manganese or zinc acetates. It is preferable to use a compound selected from one kind. Moreover, it is preferable to use ethylene glycol as the alkylene glycol used in this case. In order to promote the reaction, the depolymerization reaction tank is preferably provided with a stirrer or a self-circulation line of the depolymerization reaction tank, and the depolymerization proceeds while circulating the alkylene glycol or the depolymerization liquid.
[0018]
During this depolymerization reaction, among the dissimilar plastics contained in the polyester waste, plastics mainly composed of polyolefin such as polyethylene, polypropylene, polystyrene, etc., which have a low specific gravity with respect to the depolymerization liquid, float near the liquid surface of the depolymerization liquid. To do. Normally, different types of plastics with a specific gravity that is considerably smaller than the depolymerization solution rise and float to the surface of the depolymerization solution to such an extent that it can be easily distinguished by visual observation. It may not be said that it is floating. Further, when the amount of different plastics is larger than the liquid surface area, the different plastics may float in a state where the different plastics are crowded with respect to the narrow liquid surface. In such a case, removing the dissimilar plastic floating on the liquid level will cause the liquid level to rise and float, but because there is a dissimilar plastic on the liquid level, it may not be possible to rise to the liquid level as a result. . “Floating in the vicinity of the liquid surface” is due to these reasons, and as a result, removal of dissimilar plastics that are not floating on the liquid surface is also included in the present invention.
[0019]
These floating dissimilar plastics are removed by drawing out at the same time as the depolymerization solution in the upper layer. About this removal step, even when the depolymerization reaction of the polyalkylene terephthalate is not completely completed, even if it is in a slurry state in which the different plastics float enough to be separated or unreacted polyalkylene terephthalate remains. It can be implemented. That is, it can be carried out even when all of the polyalkylene terephthalate has undergone a depolymerization reaction or a part of the polyalkylene terephthalate has undergone a depolymerization reaction.
[0020]
In the next second step, the surface of the outer depolymerization solution is controlled while controlling the temperature of the external polymerization solution to be in the range of 120 to 180 ° C. when the solid different plastic contained in the depolymerization solution is removed from the system. This is a step of extracting a dissimilar plastic having a specific gravity smaller than that of the depolymerization solution floating in the vicinity. When separating the depolymerization liquid and the foreign matter from the depolymerization reaction tank, it is necessary to keep the temperature of the depolymerization liquid at 120 to 180 ° C. When the temperature exceeds 180 ° C., the viscosity of the different plastic increases, so that fusion occurs and it becomes difficult to extract the suspended matter from the depolymerization reaction tank. Preferably, the temperature of the depolymerization solution is controlled in the range of 130 ° C to 170 ° C. If this temperature range is maintained, the viscosity of dissimilar plastics composed mainly of polyolefin can be reduced, and the dissimilar plastics can be kept in a state that does not decrease the viscosity of the depolymerization solution while curing the dissimilar plastics. It is possible to prevent troubles in the subsequent steps. Also, when the depolymerization solution is sent to the next step, it is preferable to keep this temperature because the solution can be sent easily. In the depolymerization reaction tank, it is generally preferable to circulate the liquid in the depolymerization reaction tank using a stirrer, a circulation pump, or the like in order to promote the reaction.
[0021]
In the depolymerization reaction tank, the depolymerization reaction does not necessarily need to be carried out completely. Therefore, the depolymerization reaction can be applied even when unreacted polyalkylene terephthalate remains at the time of removal. Furthermore, if the depolymerization reaction has progressed for a certain level or more, it is possible to install a device such as a filtration or strainer at a location where the liquid is transferred from the depolymerization reaction tank to the next process.
[0022]
【Example】
The contents of the present invention will be described more specifically with reference to the following examples, but the present invention is not limited thereto. In addition, each value in an Example was calculated | required according to the following method.
[0023]
[Example 1]
50 parts of polyethylene terephthalate, 2 parts of polystyrene, 2 parts of polyethylene, 200 parts of ethylene glycol and 1.5 parts of sodium carbonate as a depolymerization catalyst were put into a dereaction polymerization tank and heated to 170 ° C. with stirring at 100 rpm. The state was kept for 1 hour. A part of the polyethylene terephthalate charged at this time reacted, the unreacted product was in a state of floating in the depolymerization solution, and polystyrene and polyethylene floated on small particles on the surface of the depolymerization solution. Stirring was once stopped in this state, and when 20 parts of the upper depolymerization liquid close to the liquid surface was extracted together with polystyrene and polyethylene, 3.8 parts of polystyrene and polyethylene were extracted and the liquid remaining in the depolymerization tank was removed. Only 0.2 parts of polyethylene and polystyrene remained. In addition, problems such as polyethylene or polystyrene adhering to the pipe and clogging of the pipe did not occur.
[0024]
[Comparative Example 1]
50 parts of polyethylene terephthalate, 2 parts of polystyrene, 2 parts of polyethylene, 200 parts of ethylene glycol and 1.5 parts of sodium carbonate as a depolymerization catalyst were put into a dereaction polymerization tank and heated to 185 ° C. with stirring at 100 rpm. Furthermore, when the state was kept at 100 rpm with stirring for 4 hours, the polyethylene terephthalate was dissolved and the depolymerization reaction was completed. At this time, the charged polystyrene and polyethylene floated on the surface of the depolymerization solution, but because of their increased viscosity, they fused together to form a large lump. In this state, stirring is once stopped, and when 20 parts of the upper depolymerization liquid close to the liquid surface is extracted together with polystyrene and polyethylene, the depolymerization liquid remaining in the dereaction polymerization tank cannot be extracted completely. Two parts remained.
[0025]
【The invention's effect】
According to the removal method of the present invention, when recovering an active ingredient from a polyester waste containing polyethylene terephthalate as a main component, different plastics having a small specific gravity contained in the polyester waste are separated and removed in a depolymerization tank. It is possible to eliminate sending to the process and prevent process troubles in the recycling process.

Claims (5)

ポリアルキレンテレフタレートを主成分とし、ポリアルキレンテレフタレートとは異種のプラスチックを含むポリエステル廃棄物から異種プラスチックを除去する方法であって、下記(1)、(2)の各工程を逐次的に通過させることを特徴とする異種プラスチック除去方法。
(1)アルキレングリコールにより解重合反応させる解重合反応工程へ投入し、該ポリアルキレンテレフタレートの一部または全部を解重合反応させて解重合液とする工程。
(2)該解重合液中に含まれる固体の異種プラスチックを系外へ除去する際に、該解重合液温度を120℃〜180℃の範囲に制御しつつ、該解重合液の液面近傍に浮遊する該解重合液よりも比重の小さな異種プラスチックを抜き出す工程。
Polyalkylene terephthalate is a main component, and polyalkylene terephthalate is a method for removing dissimilar plastics from polyester waste containing dissimilar plastics, and sequentially passing the following steps (1) and (2). A method for removing different types of plastics.
(1) A step of putting into a depolymerization reaction step of depolymerizing with an alkylene glycol and depolymerizing a part or all of the polyalkylene terephthalate to obtain a depolymerization solution.
(2) When the solid different plastic contained in the depolymerization liquid is removed from the system, the temperature of the depolymerization liquid is controlled in the range of 120 ° C. to 180 ° C. A step of extracting a different kind of plastic having a specific gravity smaller than that of the depolymerization solution floating on the surface.
解重合液温度を130℃〜170℃の範囲に制御する請求項1記載の除去方法。The removal method according to claim 1, wherein the temperature of the depolymerization solution is controlled in a range of 130 ° C to 170 ° C. アルキレングリコールがエチレングリコールである請求項1または2記載の除去方法。The removal method according to claim 1 or 2, wherein the alkylene glycol is ethylene glycol. ポリエステル廃棄物中に主成分として含まれるポリアルキレンテレフタレートがポリエチレンテレフタレートである請求項1記載の除去方法。The removal method according to claim 1, wherein the polyalkylene terephthalate contained as a main component in the polyester waste is polyethylene terephthalate. ポリエチレンテレフタレートが回収したPETボトル由来である、請求項4記載の除去方法。The removal method according to claim 4, wherein the polyethylene terephthalate is derived from a recovered PET bottle.
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WO2016123558A1 (en) 2015-01-30 2016-08-04 Resinate Materials Group, Inc. Integrated process for treating recycled streams of pet and ptt
US9850400B2 (en) 2014-08-20 2017-12-26 Resinate Materials Group, Inc. Digestion of keratin
US9896540B2 (en) 2014-08-20 2018-02-20 Resinate Materials Group, Inc. Polyester polyols from recycled polymers and waste streams
US9951171B2 (en) 2014-08-20 2018-04-24 Resinate Materials Group, Inc. Polyester polyols from recycled polymers and waste streams
JP2022184117A (en) * 2021-05-31 2022-12-13 三菱重工業株式会社 Separation system and method
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Publication number Priority date Publication date Assignee Title
US9850400B2 (en) 2014-08-20 2017-12-26 Resinate Materials Group, Inc. Digestion of keratin
US9896540B2 (en) 2014-08-20 2018-02-20 Resinate Materials Group, Inc. Polyester polyols from recycled polymers and waste streams
US9951171B2 (en) 2014-08-20 2018-04-24 Resinate Materials Group, Inc. Polyester polyols from recycled polymers and waste streams
US10030099B2 (en) 2014-08-20 2018-07-24 Resinate Materials Group, Inc. Digestion of keratin
WO2016123558A1 (en) 2015-01-30 2016-08-04 Resinate Materials Group, Inc. Integrated process for treating recycled streams of pet and ptt
US9714334B2 (en) 2015-01-30 2017-07-25 Resinate Materials Group, Inc. Integrated process for treating recycled PET and PTT materials
US9752005B2 (en) 2015-01-30 2017-09-05 Resinate Materials Group, Inc. Integrated process for treating recycled streams of PET and PTT
US10119006B2 (en) 2015-01-30 2018-11-06 Resinate Materials Group, Inc. Integrated process for treating recycled streams of PET and PTT
JP2022184117A (en) * 2021-05-31 2022-12-13 三菱重工業株式会社 Separation system and method
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