JPH1112389A - Classification and treatment of mixed waste plastics with solvent - Google Patents

Classification and treatment of mixed waste plastics with solvent

Info

Publication number
JPH1112389A
JPH1112389A JP20827197A JP20827197A JPH1112389A JP H1112389 A JPH1112389 A JP H1112389A JP 20827197 A JP20827197 A JP 20827197A JP 20827197 A JP20827197 A JP 20827197A JP H1112389 A JPH1112389 A JP H1112389A
Authority
JP
Japan
Prior art keywords
solvent
pvc
pet
mixed waste
oil
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
JP20827197A
Other languages
Japanese (ja)
Inventor
Takashi Tachibana
孝 立花
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.)
AASU RECYCLE KK
Original Assignee
AASU RECYCLE KK
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 AASU RECYCLE KK filed Critical AASU RECYCLE KK
Priority to JP20827197A priority Critical patent/JPH1112389A/en
Publication of JPH1112389A publication Critical patent/JPH1112389A/en
Pending legal-status Critical Current

Links

Classifications

    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • 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

Landscapes

  • Manufacture Of Porous Articles, And Recovery And Treatment Of Waste Products (AREA)
  • Separation, Recovery Or Treatment Of Waste Materials Containing Plastics (AREA)

Abstract

PROBLEM TO BE SOLVED: To provide a method for classifying and treating mixed waste plastics with a mixed waste plastic solvent obtained by thermally decomposing the mixed waste plastics. SOLUTION: This method for classifying and treating mixed waste plastics with a mixed waste plastic solvent comprises fractionating the thermal decomposition production oil of the waste plastics (mainly a polyolefin, a sytrenic polymer or their mixture) into a light oil and a heavy oil, treating the mixed waste plastics (PE, PP, PS, PVC or PET) or laminated films (mixed waste plastics, aluminate or paper) with the obtained light oil as a solvent to classify the mixed waste plastics into plastics (PE, PP, PS) suitable for thermal decomposition oil production and plastics (PVC, PET) unsuitable for the oil production, separating PVC with a solvent dissolving the PVC, and finally mechanically separating the left paper, aluminum and PET from each other.

Description

【発明の詳細な説明】DETAILED DESCRIPTION OF THE INVENTION

【0001】[0001]

【発明の属する技術分野】本発明は家庭,工場,スーパ
ー等から排出されるPE,PP,PS,PVC,PE
T,アルミ,紙を含くむ廃プラスチック(複合材料)を
有効に活用する油化,固形燃料化装置に関する。
The present invention relates to PE, PP, PS, PVC, PE discharged from households, factories, supermarkets and the like.
The present invention relates to an oil-forming and solid-fueling apparatus that effectively utilizes waste plastic (composite material) containing T, aluminum, and paper.

【0002】[0002]

【従来技術】混合廃プラスチック中に塩化ビニルが含ま
れるときの分別法は 1)重力分離(水槽にて) 2)PVCの塩素原子がX線を吸収する事を利用するI
R法 3)溶媒法(テトラヒドロフラン,メチルイソブチルケ
トン) 4)風力分離 1),2),4)では完全に分別出来ないため油化工程
に一部混入しそれを処理するために高価な押出機,溶融
槽を設けて脱塩化水素(脱塩率約90WT%)を行って
いる。PETボトルは収集分別で対応しているがボトル
以外でもPET樹脂が至る所に使用されているため油化
工程に一部混入してくるので油化工程内でも処置出来る
ようにしている。複合フイルムについては機械的分離が
主であり牛乳パックはカセイソーダを使用して化学的分
離が行われている。溶媒の回収は薄膜蒸発法,加熱真空
法により行われている。
2. Description of the Related Art When vinyl chloride is contained in mixed waste plastics, the separation method is as follows: 1) Gravity separation (in a water tank) 2) Utilizing the absorption of X-rays by chlorine atoms in PVC I
R method 3) Solvent method (tetrahydrofuran, methyl isobutyl ketone) 4) Wind separation 1), 2) and 4) cannot be completely separated, so they are partly mixed in the oiling process and are expensive extruders to process them And a melting tank for dehydrochlorination (desalting rate: about 90 WT%). PET bottles are collected and sorted, but since PET resin is used everywhere other than the bottles, some of them are mixed into the oiling process, so that treatment can be performed even in the oiling process. For composite films, mechanical separation is mainly used, and milk packs are chemically separated using caustic soda. The solvent is recovered by a thin film evaporation method and a heating vacuum method.

【0003】[0003]

【発明が解決しようとする課題】しかし上記法では下記
に列挙される問題点があった。 1)混合廃プラスチックを油化するときPVCが含まれ
ると装置の腐食を発生させ又多くの有機塩素化合物を含
むため製品となりえない。現在高価な押出機,溶融槽を
設けて油化工程に入る前に約90WT%脱塩化水素を行
っているが経済的,信頼性に欠ける。塩酸回収コスト高
い。 2)PETが油化装置に混入したときPETは300℃
で昇華しテレフタール酸結晶物を配管等で析出させ閉塞
させる又生成油中に結晶物が含まれ品質に悪影響を与え
る。又油化率を低下させる。 3)PVC,有機塩素化合物を含む油を燃焼すれば猛毒
のダイオキシンを発生する。現在固形燃料ではPVCは
排除している。 4)風力,重力分離は細かく破砕するため破砕,異物分
離コストが高い。特に重力分離(分離効率は高いが)は
水を使用するため乾燥,廃水処理にコストがかかる。 5)X線法はボトルには効果を発揮するがフイルムには
難しい。 6)従来の溶媒では溶媒コストが高く経済的でない。 7)複合フイルムからプラスチック,アルミ,紙を分離
する機械的法は高コストであり,牛乳パックはカセイソ
ーダーを使用しているため廃水処理が必要で又分離時間
が3時間要し効率的でない。 8)これら複合フイルム処理は現在最も簡単で低コスト
の環境負荷の大きい焼却処理が主流である。
However, the above method has the following problems. 1) When the mixed waste plastic is liquefied, if PVC is contained, it causes corrosion of the equipment and contains many organic chlorine compounds, so that it cannot be a product. At present, about 90 WT% dehydrochlorination is carried out before an oil extruder is installed with an expensive extruder and a melting tank, but it is not economical and reliable. High hydrochloric acid recovery cost. 2) When PET is mixed into the oiling device, PET is 300 ° C.
Sublimates to precipitate and block the terephthalic acid crystal by pipes and the like, and the quality is adversely affected by the inclusion of the crystal in the produced oil. It also reduces the oiling rate. 3) Burning oil containing PVC and organochlorine compounds generates highly toxic dioxins. Currently, solid fuels exclude PVC. 4) The cost of crushing and foreign matter separation is high because wind power and gravity separation crush finely. In particular, gravity separation (although the separation efficiency is high) uses water, so that drying and wastewater treatment are costly. 5) The X-ray method is effective for bottles, but is difficult for films. 6) Conventional solvents have high solvent costs and are not economical. 7) The mechanical method of separating plastic, aluminum, and paper from the composite film is expensive, and milk packs use caustic soda, so wastewater treatment is required, and the separation time is 3 hours, which is inefficient. 8) The simplest, low-cost, and high-impact incineration of these composite films is currently the mainstream.

【0004】[0004]

【問題を解決するための手段】廃プラスチック(ポリオ
レフイン,スチレン系プラスチックが主としそれらの単
体又は混合)を熱分解(温度約400℃,反応時間約4
時間)して得られた熱分解生成油を軽質油(沸点約16
0℃)と重質油に分離し軽質油を溶媒として使用する。
[Means for Solving the Problem] Waste plastics (polyolefin and styrene-based plastics are mainly used alone or in combination) are thermally decomposed (temperature about 400 ° C., reaction time about 4 hours).
Time) and convert the resulting pyrolysis oil to light oil (boiling point of about 16
0 ° C) and separated into heavy oils, and light oils are used as solvents.

【0006】PVC,PETを含む混合プラスチックと
本溶媒を約120℃の溶液中で混合接触させるとPE,
PP,PS樹脂のみ溶解しPVC,PETは溶解しない
で固体のまま存在する。溶解したPE,PP,PSはス
トレーナーを通過し油化原料となる。未溶解物PVC,
PETはストレーナーでキャッチされる。
When a mixed plastic containing PVC and PET and this solvent are mixed and contacted in a solution at about 120 ° C., PE,
Only PP and PS resins are dissolved, and PVC and PET do not dissolve and remain as a solid. The dissolved PE, PP, and PS pass through the strainer and become an oil material. Undissolved PVC,
PET is caught by a strainer.

【0007】PE,PP,PSは熱分解槽で熱分解され
簡易蒸留で軽質油と重質油に分離され軽質油は再度溶媒
として使用される。未溶解物のPVC,PETはPVC
に優れた溶解性を示す溶媒(溶解度パラメーターに近い
溶媒,例えばEDC,MEK,ジオキサン等)と混合さ
れ未溶解のPETと分離される。PVCの溶解液は加熱
真空法等でPVCと溶媒に分離しその溶媒は分離再使用
されPVCは再生樹脂原料として回収される。
[0007] PE, PP and PS are thermally decomposed in a pyrolysis tank, separated into light oil and heavy oil by simple distillation, and the light oil is used again as a solvent. Undissolved PVC and PET are PVC
And a solvent exhibiting excellent solubility (solvent having a solubility parameter close to the solubility parameter, such as EDC, MEK, dioxane, etc.) and separated from undissolved PET. A solution of PVC is separated into PVC and a solvent by a heating vacuum method or the like, and the solvent is separated and reused, and PVC is recovered as a recycled resin raw material.

【0008】複合フイルム,牛乳パックも本溶媒(熱分
解軽質油とPVCを溶解する溶媒)を使用して同条件で
処理する事によりPE,PP,PSは油化原料にPVC
は再生樹脂原料としてアルミ,紙,PETは機械的に分
離される。そうすることによりPETも再生樹脂原料に
アルミも再生アルミとして利用できる。
[0008] Composite films and milk packs are also treated under the same conditions using the present solvent (solvent that dissolves pyrolytic light oil and PVC), so that PE, PP, and PS can be converted to oily raw materials by PVC.
Aluminum, paper and PET are mechanically separated as recycled resin raw materials. By doing so, both PET and recycled resin material can be used as recycled aluminum.

【0009】[0009]

【作用及び発明の効果】本発明によれば次の効果が得ら
れる。 1)本溶媒(熱分解軽質油)は廃プラスチック熱分解か
ら得られるため非常に経済的である。 2)熱分解油化原料として不向きなPVC,PET含く
む廃プラスチックを本法で処理すれば前処理設備,油化
装置(脱塩化水素の為の高価な押出機等削除できる)が
シンプルとなり熱分解油化の経済性,信頼性が大幅に改
善される。 3)廃プラスチック中にPVC,PETが混入しても本
法を採用すれば熱分解生成油に有機塩素化合物,テレフ
タール酸結晶物が含まれず良質の製品が得られる。 4)本溶媒(熱分解軽質油)の用途は広く複合フイル
ム,牛乳パック等複合材の分離に利用できる。固形燃料
製造にも利用できる。 5)PVC,PETの分離にPVCを溶解する溶媒を使
用すれば再生PVC,PET原料と再生アルミが得られ
る。 6)本発明が実行されたなら従来困難とされていた複合
材の分離が経済的に行われるようになり廃プラスチック
のリサクル率は急上昇する。
According to the present invention, the following effects can be obtained. 1) The solvent (pyrolysis light oil) is very economical because it is obtained from pyrolysis of waste plastic. 2) If waste plastic containing PVC and PET, which are unsuitable as pyrolysis oil conversion raw materials, is treated by this method, pretreatment equipment and oil conversion equipment (expensive extruder for dehydrochlorination, etc. can be eliminated) are simplified and heat is reduced. The economics and reliability of cracking oil are greatly improved. 3) Even if PVC and PET are mixed in the waste plastic, if this method is adopted, a high-quality product can be obtained without the organic chlorine compound and terephthalic acid crystal in the pyrolysis oil. 4) The solvent (pyrolyzed light oil) can be widely used for separating composite materials such as composite films and milk packs. It can also be used for solid fuel production. 5) If a solvent that dissolves PVC is used for separation of PVC and PET, recycled PVC and PET raw materials and recycled aluminum can be obtained. 6) If the present invention is practiced, the separation of the composite material, which has been conventionally difficult, becomes economical, and the recycle rate of waste plastic rises sharply.

【0010】[0010]

【発明の実態の形態】以下本発明の実施例を図面に基と
ずいて説明する。図−1は本発明方法を実施するに好適
な装置の概略構成図である。廃プラスチック(PE,P
P,PS,PVC,PET,アルミ,紙)は破砕機10
0にて約5cmに破砕し投入機101を使用して溶解槽
102へ投入する。攪拌機103が設けられた溶解槽1
02に約120℃に加熱された熱分解軽質油(溶媒)が
溶解槽容量の約60%満たされている。溶解槽では溶媒
と廃プラスチックが攪拌混合され水分も飛ばされながら
PE,PP,PSが選択的に溶解しPVC,PET,ア
ルミ,紙は全く溶解しない。それら溶液は溶解槽槽底に
設けられたスペアー付のストレーナー104で処理され
る。溶解PE,PP,PSはストレーナーを通過しポン
プ006を介して熱分解槽007へ張り込まれる。溶解
しないPVC,PET,アルミ,紙はストレーナーでキ
ャッチされる。熱分解槽007へ張り込まれたPE,P
P,PSは温度約400℃反応時間約4時間与える事に
より熱分解生成油と残査に分離され熱分解槽底部より一
定量系外へ排出される。熱分解生成油は熱交換されなが
ら簡易蒸留等で軽質油(溶媒)と重質油に分離され軽質
油槽009,重質油槽012にストックされる。軽質油
(溶媒)は一部軽質油ポンプ010を介して加熱器01
1で温度約120℃に加熱され溶解槽に張り込まれる。
残りの軽質油は製品となる。重質油の一部と分解ガスは
燃料として使用し残りの重質油は製品となる。PVC,
PETの分離はPVCに溶解性のある例えばEDC,M
EK,ジオキサン等を溶媒として使用する。溶解したP
VCは加熱真空装置に導入され溶媒とPVCに分離され
溶媒であるシクロヘキサンは再使用される。PVC樹脂
は再生用樹脂原料として利用される。複合フイルム,牛
乳パック等も同様に処理されるがアルミ,紙,PETの
分離は機械的に分離される。
Embodiments of the present invention will be described below with reference to the drawings. FIG. 1 is a schematic configuration diagram of an apparatus suitable for carrying out the method of the present invention. Waste plastic (PE, P
P, PS, PVC, PET, aluminum, paper)
The mixture is crushed to about 5 cm at 0 and charged into a dissolution tank 102 using a charging machine 101. Dissolution tank 1 provided with stirrer 103
02, the pyrolysis light oil (solvent) heated to about 120 ° C. is filled to about 60% of the dissolution tank capacity. In the dissolving tank, PE, PP, and PS are selectively dissolved while the solvent and the waste plastic are stirred and mixed to remove water, and PVC, PET, aluminum, and paper are not dissolved at all. These solutions are processed by a strainer 104 with a spare provided at the bottom of the dissolution tank. The dissolved PE, PP, and PS pass through the strainer and are inserted into the thermal decomposition tank 007 via the pump 006. Undissolved PVC, PET, aluminum and paper are caught by the strainer. PE, P stuck in pyrolysis tank 007
By giving P and PS at a temperature of about 400 ° C. for a reaction time of about 4 hours, a certain amount of P and PS is separated from the pyrolysis oil and the residue from the bottom of the pyrolysis tank. The thermally cracked oil is separated into light oil (solvent) and heavy oil by simple distillation or the like while exchanging heat, and is stocked in the light oil tank 009 and the heavy oil tank 012. Light oil (solvent) is partially supplied to the heater 01 via the light oil pump 010.
In step 1, the mixture is heated to a temperature of about 120 ° C. and stuck into the melting tank.
The remaining light oil becomes a product. A part of heavy oil and cracked gas are used as fuel, and the remaining heavy oil becomes a product. PVC,
The separation of PET is carried out by dissolving in PVC, for example EDC, M
EK, dioxane or the like is used as a solvent. Dissolved P
VC is introduced into a heating vacuum apparatus, separated into a solvent and PVC, and cyclohexane as a solvent is reused. PVC resin is used as a resin material for regeneration. Composite films, milk packs and the like are treated in the same manner, but the separation of aluminum, paper and PET is mechanically separated.

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

【図−1】PE,PP,PS,PVC,PET,アル
ミ,紙の混合廃プラスチックの処理する好ましい実施形
態を示す。
FIG. 1 shows a preferred embodiment for treating a mixed waste plastic of PE, PP, PS, PVC, PET, aluminum and paper.

【符号の説明】[Explanation of symbols]

100 破砕機 117 アルミ
/紙/PET分離機 101 投入機 102 溶解槽 103 攪拌機 104 ストレーナー 105 熱分解槽フイードポンプ 106 熱分解槽 107 熱交換器/蒸留装置 108 軽質油槽 109 軽質油ポンプ 110 加熱器 111 重質油槽 112 重質油ポンプ 113 PVC溶解槽 114 ストレーナー(PET等キャッチ) 115 溶解PVC移送ポンプ 116 加熱真空装置(PVCの溶媒回収)
REFERENCE SIGNS LIST 100 Crusher 117 Aluminum / paper / PET separator 101 Feeder 102 Dissolution tank 103 Stirrer 104 Strainer 105 Thermal decomposition tank feed pump 106 Thermal decomposition tank 107 Heat exchanger / Distillation device 108 Light oil tank 109 Light oil pump 110 Heater 111 Heavy Oil tank 112 Heavy oil pump 113 PVC dissolving tank 114 Strainer (catch such as PET) 115 Dissolved PVC transfer pump 116 Heating vacuum device (PVC solvent recovery)

Claims (3)

【特許請求の範囲】[Claims] 【請求項1】廃プラスチック熱分解生成油のうち軽質油
を溶媒とし混合廃プラスチック即ちポリエチレン(P
E),ポリプロピレン(PP),ポリスチレン(P
S),塩化ビニル(PVC),ポリエチレンテレフタレ
ート(PET)と約120℃でこの溶媒液と接触する事
によりPE,PP,PSは本溶媒に溶解し未溶解のPV
C,PETはストレーナーで分離される。
1. A mixed waste plastic, ie, polyethylene (P), using light oil as a solvent among waste plastic pyrolysis oils.
E), polypropylene (PP), polystyrene (P
S), vinyl chloride (PVC), polyethylene terephthalate (PET) and PE, PP, PS dissolved in this solvent by contacting this solvent at about 120 ° C
C and PET are separated by a strainer.
【請求項2】そしてPVCとPETの分離はPVCに可
溶な溶媒(溶解度パラメーターに近い溶媒を選択)を使
用する。その溶媒の回収は加熱真空法等で行いその時分
離されるPVCは再生樹脂原料として再利用する。
2. Separation of PVC and PET uses a solvent which is soluble in PVC (select a solvent having a solubility parameter close to the solubility parameter). The solvent is recovered by a heating vacuum method or the like, and the PVC separated at that time is reused as a recycled resin material.
【請求項3】本溶媒(熱分解軽質油とPVCを溶解する
溶媒)で同プロセスを使用し複合フイルム,牛乳パック
等からPE,PP,PSの混合物とPVC,PET,ア
ルミ,紙をそれぞれ分離する。
3. A mixture of PE, PP, PS and PVC, PET, aluminum, and paper are separated from a composite film, a milk pack, etc. by using the same solvent (solvent that dissolves pyrolysis light oil and PVC). .
JP20827197A 1997-06-26 1997-06-26 Classification and treatment of mixed waste plastics with solvent Pending JPH1112389A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP20827197A JPH1112389A (en) 1997-06-26 1997-06-26 Classification and treatment of mixed waste plastics with solvent

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP20827197A JPH1112389A (en) 1997-06-26 1997-06-26 Classification and treatment of mixed waste plastics with solvent

Publications (1)

Publication Number Publication Date
JPH1112389A true JPH1112389A (en) 1999-01-19

Family

ID=16553487

Family Applications (1)

Application Number Title Priority Date Filing Date
JP20827197A Pending JPH1112389A (en) 1997-06-26 1997-06-26 Classification and treatment of mixed waste plastics with solvent

Country Status (1)

Country Link
JP (1) JPH1112389A (en)

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2006078097A1 (en) * 2005-01-24 2006-07-27 Korea Institute Of Industrial Technology Method of reclaiming multilayered film waste
PL444036A1 (en) * 2023-03-10 2024-09-16 Uniwersytet Łódzki Method of separating components of waste PET/PE/PET foil laminates

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2006078097A1 (en) * 2005-01-24 2006-07-27 Korea Institute Of Industrial Technology Method of reclaiming multilayered film waste
PL444036A1 (en) * 2023-03-10 2024-09-16 Uniwersytet Łódzki Method of separating components of waste PET/PE/PET foil laminates

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