[go: up one dir, main page]

JP3178095B2 - How to Recycle Painted Plastic - Google Patents

How to Recycle Painted Plastic

Info

Publication number
JP3178095B2
JP3178095B2 JP18587492A JP18587492A JP3178095B2 JP 3178095 B2 JP3178095 B2 JP 3178095B2 JP 18587492 A JP18587492 A JP 18587492A JP 18587492 A JP18587492 A JP 18587492A JP 3178095 B2 JP3178095 B2 JP 3178095B2
Authority
JP
Japan
Prior art keywords
plastic
coating film
finely pulverized
bumper
particle size
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Expired - Fee Related
Application number
JP18587492A
Other languages
Japanese (ja)
Other versions
JPH06819A (en
Inventor
尚孝 山本
徳子 大堀
宗侯 長谷川
了充 須山
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.)
Isuzu Motors Ltd
Original Assignee
Isuzu Motors 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 Isuzu Motors Ltd filed Critical Isuzu Motors Ltd
Priority to JP18587492A priority Critical patent/JP3178095B2/en
Publication of JPH06819A publication Critical patent/JPH06819A/en
Application granted granted Critical
Publication of JP3178095B2 publication Critical patent/JP3178095B2/en
Anticipated expiration legal-status Critical
Expired - Fee Related 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
    • Y02W30/52Mechanical processing of waste for the recovery of materials, e.g. crushing, shredding, separation or disassembly
    • 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

  • Processing And Handling Of Plastics And Other Materials For Molding In General (AREA)
  • Separation, Recovery Or Treatment Of Waste Materials Containing Plastics (AREA)

Description

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

【0001】[0001]

【産業上の利用分野】本発明は、表面に塗装などの表面
処理を施したしたプラスチック廃品から、プラスチック
を回収して再利用するリサイクル方法に関するものであ
る。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a recycling method for recovering and reusing plastics from waste plastics whose surfaces have been subjected to a surface treatment such as painting.

【0002】[0002]

【従来の技術】近時、自動車部品にプラスチック製品が
多く使用されるようになった。例えば、プラスチック製
バンパーの場合、表面に塗装していないバンパーでは、
成形不良品や廃車からの回収品を3mm角程度に荒粉砕
し、バージン材と混合して再度バンパーの成形に使用で
きる。これは、リサイクルしたプラスチックの物性が殆
ど低下しないから可能となるのであって、表面に塗装を
施したバンパーでは、同様な方法で回収したプラスチッ
クを再びバンパーに使用することができない。その理由
は、塗装したバンパーでは、リサイクルしたプラスチッ
ク中に粉砕した塗膜が混入することにより、プラスチッ
ク材料の耐衝撃性、伸び、表面品質などの物性が大幅に
低下し、バンパーとして必要な性能を満足することがで
きなくなるからである。したがって、成形不良品、廃車
となった車からの回収品などの塗装したプラスチックバ
ンパーは、余り物性を要求されない建築用の杭などに再
利用される外は、地面に埋めたり、燃やしたりされてお
り、環境破壊の問題がある。
2. Description of the Related Art Recently, plastic products have been frequently used for automobile parts. For example, in the case of a plastic bumper, if the bumper has no surface painted,
Defective molded products and recovered products from end-of-life vehicles are roughly pulverized to about 3 mm square, mixed with virgin material, and used again for bumper molding. This is possible because the physical properties of the recycled plastic hardly deteriorate, and in the case of a bumper whose surface is painted, the plastic recovered by the same method cannot be used again for the bumper. The reason is that, in the case of painted bumpers, the physical properties such as impact resistance, elongation, and surface quality of the plastic material are significantly reduced due to the incorporation of the crushed coating film into the recycled plastic, and the required performance as a bumper is reduced. This is because they cannot be satisfied. Therefore, painted plastic bumpers, such as defective molded products and recovered products from scrapped vehicles, are buried in the ground or burned except when reused for construction piles, etc., which do not require much physical properties. And there is a problem of environmental destruction.

【0003】特開平3−23909号公報には、ポリウ
レタンとポリ塩化ビニルが積層した廃棄物からポリウレ
タンとポリ塩化ビニルとを分離回収する方法として次の
方法が提案されている。上記の複合材廃棄物を20〜5
0mm程度の塊状物に粗粉砕し、次いでこれを高速攪拌
機で攪拌して微粉砕し、フルイにより粒径1〜2mmの
ポリウレタンと外形寸法30mm程度のシート状ポリ塩
化ビニルに分離し、ポリ塩化ビニルを回収する。
JP-A-3-23909 proposes the following method for separating and recovering polyurethane and polyvinyl chloride from waste in which polyurethane and polyvinyl chloride are laminated. 20 to 5 of the above composite waste
Roughly pulverized into a lump of about 0 mm, and then finely pulverized by stirring with a high-speed stirrer, separated into polyurethane having a particle size of 1 to 2 mm and a sheet-like polyvinyl chloride having an outer dimension of about 30 mm by a sieve. Collect.

【0004】現在塗装したプラスチックバンパーのリサ
イクルは、プラスチック部分と塗膜部分とを分離し、プ
ラスチック部分のみを回収して再利用する技術開発が進
められており、大別すると次の3種類となる。 ブラストにより塗膜を剥す方法 塗装したプラスチックバンパーの塗膜に圧縮空気と共に
研磨材を吹付け、機械的に塗膜を剥す。 溶融してスクリーンで塗膜を分離する方法 塗装したプラスチックバンパーを荒粉砕し、それを押出
機に投入してプラスチック部分を溶融する。塗膜は熱硬
化性のため押出機内では溶融しないので、押出機の出口
部にスクリーンを設置して塗膜を分離する。 化学薬品によりプラスチックから塗膜を剥離する方法 有機塩類、多価アルコール、水などの混合液を約100
℃に加熱し、この液に塗装したプラスチックバンパーの
荒粉砕品を数時間浸して塗膜を剥離する。
At present, for the recycling of painted plastic bumpers, the development of technology for separating the plastic portion and the coating film portion, recovering only the plastic portion, and reusing the plastic portion has been promoted. . A method of removing the coating film by blasting Abrasive is sprayed together with compressed air on the coated plastic bumper coating film, and the coating film is mechanically peeled off. Method of melting and separating the coating film with a screen The coated plastic bumper is roughly pulverized and put into an extruder to melt the plastic part. Since the coating film is thermosetting and does not melt in the extruder, a screen is installed at the outlet of the extruder to separate the coating film. A method of peeling a coating film from a plastic with a chemical agent A mixed solution of organic salts, polyhydric alcohol, water, etc. is used for about 100.
C. and the coated plastic bumper was immersed in this solution for several hours to remove the coating.

【0005】[0005]

【発明が解決しようとする課題】前記の方法では、研
磨材吹付けノズルと対象物との距離、吹付け角度、空気
圧、ノズルの径及び形状などの調整が非常に難しく、対
象物が平面形状であればまだしも、バンパーのような3
次元的に表面形状が変化するものでは、上記の調整が非
常に困難である。前記の方法では、押出機の出口部に
設置するスクリーンのメッシュの粗さを細かくし、粉砕
された塗膜片まで完全に分離しようとすると、押出し圧
力が高くなってスクリーンが破損してしまう。また、ス
クリーンのメッシュを粗くすると、細かい塗膜片が除去
できなくなる。前記の方法は、有機塩類が人体に有害
であるため、排水処理等の問題があって工業化が難し
い。したがって、現在までの前記開発技術は、実用化に
は至っていない。また、前記公開公報に記載された高速
攪拌機で攪拌して微粉砕する程度では、積層物の分離は
可能であっても、塗装したプラスチックの塗膜の分離を
行うことはできない。
In the above-mentioned method, it is very difficult to adjust the distance between the abrasive spray nozzle and the object, the spray angle, the air pressure, the diameter and the shape of the nozzle, and the object has a planar shape. Then still, like a bumper 3
If the surface shape changes dimensionally, the above adjustment is very difficult. In the above method, if the mesh of the screen installed at the outlet of the extruder is made finer and it is attempted to completely separate the crushed coating pieces, the extrusion pressure is increased and the screen is broken. Further, when the mesh of the screen is made coarse, it is impossible to remove fine pieces of the coating film. In the above method, since the organic salts are harmful to the human body, there is a problem such as wastewater treatment and industrialization is difficult. Therefore, the developed technology up to now has not been put to practical use. In addition, a laminate can be separated but a coated plastic film cannot be separated by a high-speed stirrer described in the above-mentioned Japanese Patent Application Laid-Open (Kokai) No. H11-27139.

【0006】本発明は、化学薬品を使用することなく塗
膜をプラスチックから剥離することを可能とし、リサイ
クル処理作業に危険が無く、また、所望の物性の回収プ
ラスチックが安価に得られる塗装プラスチックのリサイ
クル方法を提供することを目的とする。
The present invention makes it possible to remove a coating film from a plastic without using a chemical agent, so that there is no danger in a recycling process and that a recovered plastic having desired physical properties can be obtained at low cost. It aims to provide a recycling method.

【0007】[0007]

【課題を解決するための手段】本発明は、塗装プラスチ
ックの廃品を荒粉砕し、この荒粉砕品を−20℃以下に
冷却し、次いでプラスチック部の粒度分布の平均値が約
250μm以下となるまで低温雰囲気にて微粉砕し、こ
の微粉砕品を75μm以上に分級することによりプラス
チックを回収する塗装プラスチックのリサイクル方法で
ある。
SUMMARY OF THE INVENTION The present invention relates to a paint plastic.
Coarsely pulverized waste products and reduce the coarsely pulverized products to -20 ° C or lower.
This is a coated plastic recycling method in which the plastic is cooled, then finely pulverized in a low-temperature atmosphere until the average value of the particle size distribution of the plastic part becomes about 250 μm or less, and the finely pulverized product is classified into 75 μm or more to recover the plastic. .

【0008】[0008]

【作用】上記のような微粉砕を行うと、塗膜をプラスチ
ック部から剥すことができ、塗膜とプラスチックの硬度
が異なるため、両者の粒度分布の異なる微粉砕品が得ら
れ、塗膜の粒度はプラスチックの粒度に比べて格段に小
さくなる。この微粉砕品を75μm以上に分級すること
により、塗膜を除去したプラスチックが得られ、75μ
m以下は、殆どが塗膜の微粉砕品となる。
When the above-mentioned pulverization is performed, the coating film can be peeled off from the plastic part, and since the hardness of the coating film and the plastic are different, finely pulverized products having different particle size distributions of both can be obtained. The particle size is much smaller than that of the plastic. By classifying this finely pulverized product to 75 μm or more, a plastic from which the coating film has been removed is obtained.
If it is less than m, most of the film is finely pulverized.

【0009】[0009]

【実施例】本発明のリサイクル方法の概要を、塗装した
プラスチックバンパーのリサイクルについて説明する。
廃品の塗装したプラスチックバンパーを、先ず3mm角
程度に荒粉砕し、次いで微粉砕を行なう。この微粉砕
は、プラスチック部の粒度分布の平均値が約250μm
以下となるまで実施する。このような微粉砕を行うと、
塗膜をプラスチック部から剥すことができ、塗膜とプラ
スチックの硬度が異なるため、両者の粒度分布の異なる
微粉砕品が得られ、塗膜の粒度はプラスチックの粒度に
比べて格段に小さくなる。この微粉砕品を75μm以上
に分級することにより、塗膜を除去したプラスチックが
得られる。75μm以下は、殆どが塗膜の微粉砕品とな
る。75μm以上に分級したプラスチック微粉砕品を、
更に調音波による浮沈分離処理を行うと、プラスチック
から塗膜を完全に除去することができ、浮沈分離された
プラスチックは、塗膜の混入がないので再びバンパーの
材料としてして使用したときに物性の低下が全くなく、
プラスチックのリサイクルが実用化できる。
DETAILED DESCRIPTION OF THE PREFERRED EMBODIMENTS The outline of the recycling method of the present invention will be described with reference to recycling of a coated plastic bumper.
First, the waste plastic bumper is roughly pulverized to about 3 mm square, and then finely pulverized. In this pulverization, the average value of the particle size distribution of the plastic part was about 250 μm.
Perform until the following. When such fine grinding is performed,
The coating film can be peeled off from the plastic part, and since the hardness of the coating film and the plastic are different, finely pulverized products having different particle size distributions can be obtained, and the particle size of the coating film is much smaller than that of the plastic. By classifying this finely pulverized product to 75 μm or more, a plastic from which the coating film has been removed can be obtained. Almost 75 μm or less is a finely pulverized coating film. Plastic finely pulverized product classified to 75 μm or more,
Furthermore, if the floatation / sedimentation treatment is performed by using sound waves, the coating film can be completely removed from the plastic, and the floating / sedimentation separated plastic has no physical properties when used as a bumper material again because there is no contamination of the coating film. Without any decrease in
Practical use of plastic recycling.

【0010】次に、試験例を示す。 試料のプラスチックバンパーの材質 プラスチック:ポリプロピレン樹脂 塗料:プライマー、ベースともにポリエステル系メラミ
ン樹脂の焼付け塗料 超低温雰囲気での微粉砕 粉砕機:ピンミル 温度 :液体窒素で−20〜−60℃に冷却 処理 荒粉砕した試料をピンミルに投入する前に、液体窒素中
に浸して冷却し、ピンミルの周速190/secで試料
を粉砕し、プラスチック部分の平均粒度が約250μm
となるまで粉砕を継続する。得られた微粉砕品は、塗膜
がプラスチック部から完全に剥がされ、図1に示すよう
に、塗膜2の粒度分布の平均値は約20μm、プラスチ
ック1の粒度分布の平均値は約250μmとなり、それ
らの粒径の分布範囲が離れる。
Next, test examples will be described. Material of sample plastic bumper Plastic: Polypropylene resin Coating: Baking paint of polyester melamine resin for both primer and base Ultra-low temperature pulverization Crusher: Pin mill Temperature: Cooling to -20 to -60 ° C with liquid nitrogen Rough pulverization Before the sample is put into the pin mill, it is immersed in liquid nitrogen and cooled, and the sample is pulverized at a peripheral speed of the pin mill of 190 / sec.
Continue grinding until In the obtained finely pulverized product, the coating film was completely peeled off from the plastic part. As shown in FIG. 1, the average value of the particle size distribution of the coating film 2 was about 20 μm, and the average value of the particle size distribution of the plastic 1 was about 250 μm. And the distribution ranges of those particle sizes are separated.

【0011】上記の微粉砕した塗膜とプラスチックの混
合物の材料物性は、荒粉砕したままのものより格段に向
上する。その物性の比較試験の結果を表1に示す。表1
から、上記の条件で微粉砕した塗膜とプラスチックの混
合物は、バンパーの材料としてはそのまま使用できない
までも、物性の余り必要とされない部品にはそのまま使
用可能である。プラスチックは熱可塑性樹脂であればよ
く、塗料は通常の焼付け塗料であってもよい。また粉砕
機は、ディスクミル、ハンマーミル、軸流型・渦流型の
低温で粉砕可能なものが使用できる。微粉砕処理は、粗
粉砕した材料を−20〜−250の範囲で冷却し、周
速50〜300m/secの範囲で微粉砕するようにし
てもよい。
The material properties of the above-mentioned mixture of the finely pulverized coating film and the plastic are remarkably improved as compared with those of the roughly pulverized film. Table 1 shows the results of the comparison test of the physical properties. Table 1
Therefore, the mixture of the coating film and the plastic finely pulverized under the above-mentioned conditions can be used as it is for a part that does not require much physical properties, even if it cannot be used as a material for a bumper. The plastic may be a thermoplastic resin, and the paint may be a normal baking paint. As the crusher, a disk mill, a hammer mill, an axial flow type or a vortex type which can be crushed at a low temperature can be used. In the fine pulverization, the coarsely pulverized material may be cooled in a range of -20 to -250 ° C and finely pulverized in a range of a peripheral speed of 50 to 300 m / sec.

【0012】[0012]

【表1】 注 試料1:プラスチックのみのバージン材 試料2:塗装したプラスチックバンパーを荒粉砕し、そ
れを再成形した材料 試料3:塗装したプラスチックバンパーを荒粉砕後、更
に前記の条件で微粉砕した混合微粉砕品を再成形した材
[Table 1] Note Sample 1: Virgin material made of plastic only Sample 2: A material obtained by roughly pulverizing a painted plastic bumper and reshaping it Sample 3: A mixed and finely pulverized material obtained by roughly pulverizing a painted plastic bumper and then pulverizing under the above-mentioned conditions. Reformed material

【0013】前記の微粉砕した資料を200メッシュ
(目の粗さ約75μm)のスクリーンを使用して分級す
ると、塗膜粒はスクリーンを通過し、プラスチック粒は
スクリーン上に残り、ほぼ微粉砕された塗膜を除去する
ことができる。ただし、このプラスチック粒には、図2
に示すように、平均粒度250μmのプラスチック粒子
3の周りに平均粒度20μmの微細な塗膜粒子4が静電
気により付着した状態となるので、プラスチック粒から
塗膜粒を完全に除去することはできない。塗膜粒を完全
に除去するには、後記する浮沈分離を行う。表2に、上
記の微粉砕品を75μm以下、75〜250μm及び2
50μm以上の3種に分級した材料の物性を示す。75
μm以下に分級された材料は、殆どが塗膜の微粉砕品で
あり、75〜250μm及び250μm以上の材料は、
殆どがプラスチックの微粉砕品となる。表2から明らか
なように、75〜250μmに分級した材料は、バンパ
ーに使用できないまでも、相当物性の高い部品に再使用
が可能である。250μm以上に分級された材料は、塗
膜の混入料が非常に少なくなり、バンパーに再使用して
も問題は生じない。
When the above-mentioned finely ground material is classified using a 200-mesh (mesh coarseness: about 75 μm) screen, the coating particles pass through the screen, and the plastic particles remain on the screen, and are almost finely ground. Can be removed. However, this plastic grain has
As shown in (1), fine coating particles 4 having an average particle size of 20 μm are attached around the plastic particles 3 having an average particle size of 250 μm due to static electricity, so that the coating particles cannot be completely removed from the plastic particles. In order to completely remove the coating film grains, float separation is performed as described below. Table 2 shows that the above pulverized product was 75 μm or less, 75 to 250 μm and 2 μm.
The physical properties of the material classified into three types of 50 μm or more are shown. 75
Most of the materials classified to μm or less are finely pulverized products of coating films, and materials of 75 to 250 μm and 250 μm or more are
Most of them are finely pulverized plastic products. As is evident from Table 2, the materials classified to 75 to 250 μm can be reused for parts having high physical properties even if they cannot be used for bumpers. Materials classified to 250 μm or more have very little contamination in the coating film, and do not cause any problems when reused for bumpers.

【0014】[0014]

【表2】 注 試料4:75μm以下に分級した微粉砕品を再成形
した材料 試料5:75〜250μmに分級した微粉砕品を再成形
した材料 試料6:250μm以上に分級した微粉砕品を再成形し
た材料
[Table 2] * Sample 4: Reformed material of finely pulverized product classified to 75 μm or less Sample 5: Material of reshaped finely pulverized product classified to 75 to 250 μm Sample 6: Material of reshaped finely pulverized product classified to 250 μm or more

【0015】プラスチック粒子から塗膜粒を完全に除去
するには、次の浮沈分離を行う。プラスチックの比重は
約0.9、塗膜の比重は約1.4であるので、微粉砕品
を比重約1の液に浸し、両者の比重差を利用して分離す
る。この浮沈分離を効率よく行うには、液の攪拌、海面
活性剤の添加が有効であり、特に超音波の使用が有効
で、75〜250μmに分級した微粉砕品を、更に超音
波による浮沈分離した材料の物性を表3に示す。この塗
膜部を完全に除去した再生プラスチック材料の物性は、
バージン材の物性(表1の試料1)とほぼ同じとなる。
In order to completely remove the coating particles from the plastic particles, the following flotation separation is performed. Since the specific gravity of the plastic is about 0.9 and the specific gravity of the coating film is about 1.4, the finely pulverized product is immersed in a liquid having a specific gravity of about 1 and separated using the difference in specific gravity between the two. In order to carry out the flotation efficiently, it is effective to agitate the liquid and add a surfactant. Particularly, it is effective to use ultrasonic waves. The finely pulverized product classified to 75 to 250 μm is further separated by flotation by ultrasonic waves. Table 3 shows the physical properties of the obtained materials. The physical properties of the recycled plastic material from which the coating has been completely removed are:
It is almost the same as the physical properties of the virgin material (Sample 1 in Table 1).

【0016】[0016]

【表3】 注 試料7:75〜250μmに分級した微粉砕品を、
超音波による浮沈分離を行い、塗膜部を完全に除去した
再生プラスチック材料
[Table 3] Note Sample 7: Finely pulverized product classified to 75 to 250 μm
Recycled plastic material from which the coating is completely removed by floating separation using ultrasonic waves

【0017】上記の実施例では、塗装したプラスチック
バンパーについて説明したが、自動車関係部品では、ホ
イルカバーのリサイクルにも適用でき、また自動車以外
でも塗装などの表面処理を施したプラスチック部品から
プラスチックを回収してリサイクルができる。
In the above embodiment, a painted plastic bumper has been described. However, in the case of automobile-related parts, the present invention can also be applied to recycling of a foil cover, and in addition to automobiles, plastic can be recovered from plastic parts subjected to surface treatment such as painting. And can be recycled.

【0018】[0018]

【発明の効果】本発明は、化学薬品を使用せずに塗膜な
どをプラスチックから剥離することが可能となるので、
排水処理施設の無い工場でのリサイクル処理が可能とな
り、作業に危険が無く、環境破壊の問題も生じない。ま
た、塗膜の多少混入したものから、塗膜を完全に除去し
たプラスチックまで各種の物性の回収品が容易に得られ
るので、再利用対象物に応じて分級、分離方法を選択し
て、安いコストでプラスチックのリサイクルが可能とな
る。
According to the present invention, it is possible to peel a coating film or the like from a plastic without using a chemical agent.
Recycling at a factory without a wastewater treatment facility becomes possible, and there is no danger in work and no problem of environmental destruction. In addition, it is easy to obtain recovered products of various physical properties from plastics with completely removed paint film to plastics with some paint film mixed in. Plastics can be recycled at low cost.

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

【図1】本発明により微粉砕された樹脂と塗膜の粒度分
布を示す図。
FIG. 1 is a diagram showing the particle size distribution of a resin and a coating film finely pulverized according to the present invention.

【図2】本発明により微粉砕された樹脂粒と塗膜粒の状
態を示す図。
FIG. 2 is a diagram showing a state of resin particles and coating film particles finely pulverized according to the present invention.

【符号の説明】[Explanation of symbols]

3 微粉砕された樹脂粒 4 微粉砕された塗膜粒 3 Finely ground resin particles 4 Finely ground coating particles

───────────────────────────────────────────────────── フロントページの続き (72)発明者 須山 了充 神奈川県藤沢市土棚8番地 株式会社い すゞ中央研究所内 (56)参考文献 特開 平3−23909(JP,A) (58)調査した分野(Int.Cl.7,DB名) B29B 17/00 C08J 11/00 - 11/28 ────────────────────────────────────────────────── ─── Continuation of the front page (72) Inventor Ryomitsu Suyama 8 Tsuchiya, Fujisawa City, Kanagawa Prefecture Isuzu Central Research Institute Co., Ltd. (56) References JP-A-3-23909 (JP, A) (58) Survey Field (Int.Cl. 7 , DB name) B29B 17/00 C08J 11/00-11/28

Claims (1)

(57)【特許請求の範囲】(57) [Claims] 【請求項1】 塗装プラスチックの廃品を荒粉砕し、
の荒粉砕品を−20℃以下に冷し、次いでプラスチッ
ク部の粒度分布の平均値が約250μm以下となるまで
低温雰囲気にて微粉砕し、この微粉砕品を75μm以上
に分級することによりプラスチックを回収することを特
徴とする塗装プラスチックのリサイクル方法。
[Claim 1] a waste of painted plastic and rough grinding, this
Rough ground product was cooling to -20 ° C. or less, and then to an average value of the particle size distribution of the plastic portion is approximately 250μm following
A method for recycling coated plastics, comprising finely pulverizing in a low-temperature atmosphere, and collecting the plastic by classifying the finely pulverized product to 75 μm or more.
JP18587492A 1992-06-19 1992-06-19 How to Recycle Painted Plastic Expired - Fee Related JP3178095B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP18587492A JP3178095B2 (en) 1992-06-19 1992-06-19 How to Recycle Painted Plastic

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP18587492A JP3178095B2 (en) 1992-06-19 1992-06-19 How to Recycle Painted Plastic

Publications (2)

Publication Number Publication Date
JPH06819A JPH06819A (en) 1994-01-11
JP3178095B2 true JP3178095B2 (en) 2001-06-18

Family

ID=16178395

Family Applications (1)

Application Number Title Priority Date Filing Date
JP18587492A Expired - Fee Related JP3178095B2 (en) 1992-06-19 1992-06-19 How to Recycle Painted Plastic

Country Status (1)

Country Link
JP (1) JP3178095B2 (en)

Families Citing this family (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2730409B2 (en) * 1992-06-25 1998-03-25 住友化学工業株式会社 How to collect resin for recycling
US5661095A (en) * 1995-06-06 1997-08-26 Quantum Chemical Corporation Olefin polymerization catalyst component supported on a copolymer of an olefin and an unsaturated silane
JP5867122B2 (en) * 2012-02-02 2016-02-24 セイコーエプソン株式会社 Tape printer and control method of tape printer
CN112477047B (en) * 2020-11-10 2022-03-29 湖南吉人住工装配式建筑有限公司 Secondary processing method of polystyrene foam board for building material
JP7401015B1 (en) * 2023-04-17 2023-12-19 東洋インキScホールディングス株式会社 Separation and recovery method of plastic base materials

Also Published As

Publication number Publication date
JPH06819A (en) 1994-01-11

Similar Documents

Publication Publication Date Title
JP3279732B2 (en) How to Recycle Plastic from Varnished Plastic Parts
US5443157A (en) Automobile shredder residue (ASR) separation and recycling system
EP0745465A2 (en) Arrangement for polishing and size-regulation in a process for pulverization and separation
WO1997049780A1 (en) Process and apparatus for the preparation of fine powders
EP0796709A1 (en) Process for regenerating laminated thermoplastic molded resin articles and apparatus for regenerating the same background of the invention
JP3178095B2 (en) How to Recycle Painted Plastic
EP0469270B1 (en) Method for recovering PVC and urethane foam from automotive interior trim waste
JP3117808B2 (en) Coating removal method
US6474574B1 (en) Process for removing paint from polymeric materials
US5566888A (en) Method and an apparatus for recycling a resin component
US5468779A (en) Method for recycling painted plastic materials
JP3275654B2 (en) Method and apparatus for separating shredder dust
JPH07256641A (en) Method for recycling coated resin product
US5449123A (en) Method and apparatus for pulverizing scrapped fiber reinforced thermosetting plastic materials
EP0508042B1 (en) Method and apparatus for pulverizing difficult to crush plastic materials
JP3177373B2 (en) How to recycle painted resin products
JP2829236B2 (en) How to recycle painted resin products
EP1866136B1 (en) Method for recovering polymer materials and metallic materials constituting panel instruments of manually dismantled end-of-life motor vehicles
JPH11277537A (en) Apparatus and method for peeling laminated resin material
JPH0642812Y2 (en) Recycler for synthetic resin pieces
KR101428545B1 (en) Method of recycling coated plastic products
JP3228597B2 (en) Method and apparatus for recycling resin parts
JPH08309750A (en) Recycling of resin product
JP4377045B2 (en) Blasting projection material and recycling method of waste tires
JPH0623752A (en) Classifying method and its device for laminated composite resin having difference in composition

Legal Events

Date Code Title Description
FPAY Renewal fee payment (event date is renewal date of database)

Free format text: PAYMENT UNTIL: 20080413

Year of fee payment: 7

FPAY Renewal fee payment (event date is renewal date of database)

Free format text: PAYMENT UNTIL: 20090413

Year of fee payment: 8

LAPS Cancellation because of no payment of annual fees