JPH11116727A - Method for recovering metal and resin component from metal/plastic composite - Google Patents

Method for recovering metal and resin component from metal/plastic composite

Info

Publication number
JPH11116727A
JPH11116727A JP28842297A JP28842297A JPH11116727A JP H11116727 A JPH11116727 A JP H11116727A JP 28842297 A JP28842297 A JP 28842297A JP 28842297 A JP28842297 A JP 28842297A JP H11116727 A JPH11116727 A JP H11116727A
Authority
JP
Japan
Prior art keywords
metal
plastic
fluidized bed
composite
waste
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
JP28842297A
Other languages
Japanese (ja)
Inventor
Toshihiko Okada
敏彦 岡田
Minoru Asanuma
稔 浅沼
Tsutomu Shikada
勉 鹿田
Tatsuro Ariyama
達郎 有山
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.)
JFE Engineering Corp
Original Assignee
NKK Corp
Nippon Kokan 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 NKK Corp, Nippon Kokan Ltd filed Critical NKK Corp
Priority to JP28842297A priority Critical patent/JPH11116727A/en
Publication of JPH11116727A publication Critical patent/JPH11116727A/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
    • Y02PCLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
    • Y02P20/00Technologies relating to chemical industry
    • Y02P20/141Feedstock
    • Y02P20/143Feedstock the feedstock being recycled material, e.g. plastics
    • 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

Abstract

PROBLEM TO BE SOLVED: To provide a means of efficiently processing a metal/plastic composite of, e.g. a scrapped vehicle to realize the recovery and utilization of a metal to thereby reduce the environmental pollution caused by discarding a metal/ plastic composite. SOLUTION: A metal/plastic composite is immersed in a powder fluidized bed at 200-800 deg.C containing a plastic decomposition catalyst to decompose or melt the plastic component in the composite to transfer it into the fluidized bed, and the fluidized bed is then separated. It is desirable that the powder fluidized bed comprises a plastic decomposition catalyst.

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、廃プラスチックの
処理方法に関し、特に廃自動車のような金属と多種類の
プラスチックが互いに入り組んだ形状の金属複合廃プラ
スチックを迅速に簡便に処理して、そこに含まれている
金属を金属源として、そしてプラスチックを燃料等とし
て回収する方法に関する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a method for treating waste plastic, and more particularly to a method for quickly and easily treating a metal composite waste plastic in which a metal such as a scrap car and various kinds of plastics are intricately intermingled. The present invention relates to a method for recovering a metal contained in a fuel as a metal source and a plastic as fuel or the like.

【0002】[0002]

【従来の技術】近年、産業廃棄物や一般廃棄物としてプ
ラスチック等の合成樹脂類が増加しており、その処理が
社会的、環境上、大きな問題となっている。なかでも、
その構成成分であるプラスチックは燃焼時に発生する発
熱量が高く、焼却処理した場合の焼却炉の炉壁を傷める
等の問題から専用の焼却設備を必要とすることや、ダス
ト中に含まれる亜鉛や鉛等の有害な金属もその回収・固
定化技術が必要となる等の問題がある。かかる状況下で
現状は投棄処理されているが、投棄は埋立て地の地盤の
低下をもたらすと共に、環境対策上好ましくない。か
つ、昨今では処理費の増加とともに埋め立て地用の用地
確保が社会問題となりつつあり、このため投棄によらな
い金属複合廃プラスチックの大量処理方法の開発が切望
されている。
2. Description of the Related Art In recent years, synthetic resins such as plastics have been increasing as industrial wastes and general wastes, and their disposal has become a serious social and environmental problem. Above all,
Plastic, which is a component of the incinerator, generates a large amount of heat when it is burned, and requires special incineration equipment due to problems such as damage to the walls of the incinerator when incinerated. Harmful metals such as lead also have problems such as the need for their recovery and immobilization technology. Under such circumstances, dumping is currently performed. However, dumping causes deterioration of the landfill and is not preferable in terms of environmental measures. In recent years, with the increase in disposal costs, securing land for landfills has become a social problem. For this reason, the development of a large-scale treatment method of metal-composite waste plastic without dumping has been desired.

【0003】この廃プラスチックの処理方法として、2
00℃ないし400℃の融点を有する低沸点金属または
合金を加熱・溶融し、その中に廃プラスチックを一定時
間浸漬、分解する方法が知られている(特開昭50−9
677号公報)。この方法は、ポリ塩化ビニル系樹脂を
焼却炉で処理すると有害な塩化水素が発生するので、焼
却に先立ってこれを脱塩化水素する方法として開発され
たものである。
As a method for treating this waste plastic, 2
There is known a method of heating and melting a low-boiling metal or alloy having a melting point of 00 ° C. to 400 ° C., and immersing and decomposing waste plastic for a certain period of time (Japanese Patent Laid-Open No. 50-9 / 1988)
677). This method has been developed as a method for dehydrochlorinating a polyvinyl chloride resin prior to incineration because harmful hydrogen chloride is generated when the resin is treated in an incinerator.

【0004】また、食用油廃液を溶媒としてポリエチレ
ン等接着性を有する樹脂を金属素材から除去し、金属を
採り出す方法が知られている(特開平5−147041
号公報)。同様な方法として、プラスチック材が流動化
する温度250〜300℃の溶融塩を用い、該溶融塩を
加熱によって前記温度に制御し、さらに溶融塩を前記温
度より2℃〜5℃高く加熱した雰囲気中にプラスチック
廃棄物を投入することによりプラスチック廃棄物を分離
し、溶融塩の液面上に流動化したプラスチック材を浮上
せしめるとともに、液面下に金属材やガラス材を沈降さ
せ、プラスチック材と金属材やガラス材をそれぞれ採り
出すプラスチック廃棄物の溶融塩による分離回収方法も
知られている(特開平8−108165号公報)。
Further, a method is known in which an edible oil waste liquid is used as a solvent to remove an adhesive resin such as polyethylene from a metal material to extract the metal (Japanese Patent Laid-Open No. 5-147041).
No.). As a similar method, using a molten salt at a temperature of 250 to 300 ° C. at which the plastic material is fluidized, controlling the molten salt to the above temperature by heating, and further heating the molten salt to 2 ° C. to 5 ° C. higher than the above temperature The plastic waste is separated by pouring the plastic waste into it, and the plastic material that has been fluidized floats on the liquid surface of the molten salt, and metal and glass materials settle below the liquid surface, and There is also known a method of separating and recovering a plastic waste from a metal material or a glass material by using a molten salt (Japanese Patent Laid-Open No. 8-108165).

【0005】シュレッダーダスト処理に関する技術開発
も鋭意検討されており、減容化を始め、発電を含めた焼
却溶融炉による焼却やガス化処理等が開発されつつあ
る。
[0005] Technology development relating to shredder dust treatment is also being studied diligently, and volume reduction, incineration using an incineration melting furnace including power generation, gasification treatment, and the like are being developed.

【0006】[0006]

【発明が解決しようとする課題】上記先行技術では、特
定の樹脂と金属の複合物から特定の媒体によってプラス
チックを分離し、プラスチックの再利用を行うものであ
る。他方、自動車、家電製品、OA機器などには多種類
のプラスチックの他、ガラス強化複合材料を始め、多く
の複合材料も使用されている。使用されている金属も各
種鋼板、棒鋼等の鋼材の他にアルミ、銅、亜鉛、鉛等多
種類に上がる。このような金属樹脂複合廃棄物からマテ
リアルサイクルを行うにはこれらの先行技術では多くの
問題がある。
In the above prior art, plastic is separated from a composite of a specific resin and a metal by a specific medium, and the plastic is reused. On the other hand, many kinds of composite materials such as glass-reinforced composite materials are used in automobiles, home electric appliances, OA equipment, and the like, in addition to various types of plastics. The metals used are of various types such as aluminum, copper, zinc, and lead, in addition to various steel materials such as steel plates and steel bars. Performing a material cycle from such a metal-resin composite waste has many problems in these prior arts.

【0007】例えば、特開昭50−9677号公報のよ
うに溶融金属を溶融液体として使用した場合は金属の精
錬過程で有害となる成分が金属に同伴するため、好まし
くない。また、溶融塩を用いた場合には、回収される金
属に溶融塩の成分であるアルカリが同伴され、溶融炉炉
壁の劣化を引き起こすがその対応は考慮されていない。
For example, when a molten metal is used as a molten liquid as disclosed in Japanese Patent Application Laid-Open No. 50-9677, components harmful in the refining process of the metal accompany the metal, which is not preferable. Further, when a molten salt is used, an alkali which is a component of the molten salt is entrained in the metal to be recovered, causing deterioration of the furnace wall of the melting furnace.

【0008】さらに、経済的に金属およびプラスチック
を回収するには溶融液体の効率的な分離、再生が不可欠
であるが上記先行技術ではこの対策も考慮されていな
い。特に、溶融金属を用いた場合にはポリ塩化ビニルの
分解で発生する塩化水素との反応で溶融金属が塩化物と
なるためその再生は極めて非効率的である。
Furthermore, efficient separation and regeneration of a molten liquid is indispensable for economically recovering metals and plastics, but this prior art does not consider this measure. In particular, when a molten metal is used, the regeneration of the molten metal is extremely inefficient because the molten metal is converted into chloride by a reaction with hydrogen chloride generated by decomposition of polyvinyl chloride.

【0009】また、溶融塩の場合は処理する過程で複合
材料として使用されているプラスチックはその密度が高
くなるため溶融塩中にプラスチックが残留し、浮上分離
ができない場合があり、浮上分離しても、その利用には
粉砕工程が必要であり、燃料として利用する場合、多種
類の樹脂、複合材料を含む廃棄物には適用できない。さ
らに、金属複合廃プラスチックから溶出した金属により
溶融塩の粘度等の物理的性質が変化することも考えら
れ、これらを除去再生することも極めて困難である。さ
らに、ポリプロピレンやポリエチレンは熱安定性に優れ
るため、400℃以上の処理温度が必要になり、硝酸塩
溶融塩の場合はNOxが発生するため、作業上に問題が
ある。
In the case of a molten salt, the plastic used as a composite material in the process of processing has a high density, so that the plastic remains in the molten salt and may not be able to float and separate. However, its use requires a pulverizing step, and when used as fuel, it cannot be applied to waste containing various types of resins and composite materials. Further, physical properties such as viscosity of the molten salt may change due to metals eluted from the metal composite waste plastic, and it is extremely difficult to remove and regenerate them. Furthermore, since polypropylene and polyethylene have excellent thermal stability, a treatment temperature of 400 ° C. or higher is required. In the case of a molten nitrate, NOx is generated, which poses a problem in operation.

【0010】本発明は、多種類の材料からなる金属複合
廃プラスチックから金属とプラスチック成分を効率よく
分離しマテリアルリサイクルを可能とする金属および樹
脂成分の回収方法を提供することを目的としている。
It is an object of the present invention to provide a method for recovering metal and resin components, which enables metal and plastic components to be efficiently separated from metal-composite waste plastics composed of various types of materials and enables material recycling.

【0011】[0011]

【課題を解決するための手段】本発明は上記課題を解決
するべくなされたものであり、金属複合プラスチック
を、プラスチック分解触媒を含有する200〜800℃
の粉体流動床に浸漬して該金属複合プラスチック中のプ
ラスチック成分を分解または溶融して該流動床中へ移行
させ、次いで該流動床を分離することを特徴とする金属
複合プラスチックからの金属および樹脂成分の回収方法
によってかかる目的を達成したものである。
DISCLOSURE OF THE INVENTION The present invention has been made to solve the above-mentioned problems, and is intended to convert a metal composite plastic to 200 to 800 ° C. containing a plastic decomposition catalyst.
A metal component from the metal composite plastic, characterized by decomposing or melting the plastic component in the metal composite plastic by transferring it into the fluidized bed, and then separating the fluidized bed. This object has been achieved by a method for recovering a resin component.

【0012】[0012]

【発明の実施の形態】本発明を適用し得る金属複合廃プ
ラスチックの種類は問わないが、例えば、廃自動車、廃
家電製品、廃OA機器などが適用可能である。これらの
金属複合廃プラスチックはそのままでも処理可能である
が、シュレッダー等により細片化したものであってもよ
い。細片の大きさは1〜100mm程度、特に2〜20
mm程度とすることが好ましい。
DETAILED DESCRIPTION OF THE PREFERRED EMBODIMENTS The type of waste metal composite plastic to which the present invention can be applied is not limited. For example, waste automobiles, waste home appliances, waste OA equipment and the like can be applied. These metal-composite waste plastics can be processed as they are, but may be shredded with a shredder or the like. The size of the strip is about 1 to 100 mm, especially 2 to 20 mm
mm is preferable.

【0013】プラスチック分解触媒としては、ルイス
酸、ブレンステッド酸等の酸触媒が使用可能であり、工
業的に使用されているシリカ・アルミナ系やゼオライト
系のFCC触媒、水素化分解用触媒等の固体酸等が使用
可能である。分解触媒は処理後に回収し、再利用するこ
とが望ましいが、工業的に使用済みの触媒をワンウェイ
で使用することも好ましい。再生には酸化処理する再生
塔を用いることができる。このプラスチック分解触媒は
使用温度でも固体の粉粒体であり、平均粒径が0.01
〜10mm程度、好ましくは0.02〜5mmのものが
適当である。
As the plastic decomposition catalyst, acid catalysts such as Lewis acid and Bronsted acid can be used, and silica-alumina-based or zeolite-based FCC catalysts and hydrogenolysis catalysts which are industrially used are used. Solid acids and the like can be used. Although it is desirable that the cracking catalyst be recovered after treatment and reused, it is also preferable to use an industrially used catalyst in one way. A regeneration tower for performing an oxidation treatment can be used for the regeneration. This plastic decomposition catalyst is a solid powder even at the operating temperature, and has an average particle size of 0.01.
A thickness of about 10 to 10 mm, preferably 0.02 to 5 mm is suitable.

【0014】流動床を形成する粒子はプラスチック分解
触媒のみであってもよく、他の粒子との混合物であって
もよい。他の粒子も使用温度で固体であって流動床の流
動性を向上させかつプラスチック分解触媒の性能を低下
させないものであり、例えば、珪砂、アルミナ粉、ビー
ズ等を使用することができる。他の粒子の平均粒径は
0.1〜50mm程度、好ましくは0.5〜30mm程
度のものが適当である。他の粒子の使用量は流動床構成
粒子全体の99重量%以下、好ましくは95〜5重量%
程度が適当である。
The particles forming the fluidized bed may be only a plastic cracking catalyst, or may be a mixture with other particles. Other particles are also solid at the operating temperature and improve the fluidity of the fluidized bed and do not decrease the performance of the plastic cracking catalyst. For example, silica sand, alumina powder, beads, and the like can be used. The average particle size of the other particles is about 0.1 to 50 mm, preferably about 0.5 to 30 mm. The amount of other particles used is 99% by weight or less, preferably 95 to 5% by weight of the total particles constituting the fluidized bed.
The degree is appropriate.

【0015】流動床を収容する分解炉は公知の各種のも
のを使用することができ、例えばサンドバスを使用でき
る。
As the cracking furnace accommodating the fluidized bed, various known ones can be used. For example, a sand bath can be used.

【0016】流動床の流動媒体は原則として気体であ
り、ダイオキシン発生防止のため窒素、アルゴン等の非
酸化性ガスが好ましい。
The fluid medium in the fluidized bed is a gas in principle, and a non-oxidizing gas such as nitrogen or argon is preferable for preventing generation of dioxin.

【0017】処理温度と滞留時間は通常プラスチックの
分解が十分に進行するように定められ、これはプラスチ
ックの種類、使用量によって異なるが、200〜800
℃程度、好ましくは250〜700℃、より好ましくは
350〜500℃で、0.5〜30分間程度、好ましく
は1.5〜15分程度が適当である。この時、プラスチ
ックの種類により分解挙動は異なるが、おおむね、溶融
し、また接触分解によるプラスチック主鎖の切断、低分
子化、およびガス化が生起し、分解された分子はガスお
よび分解油として系外に排出され金属から完全に分離さ
れる。得られるガスや分解油は金属の還元用ガスや燃料
として利用することが可能である。次に分解炉から取り
出した金属は付着している触媒を熱風吹き付けによって
除去する。なお、空容積が大きいときは、回収した金属
を溶解する溶解炉の効率的使用のためプレス等で適当な
大きさまで圧縮するのがよい。
The processing temperature and the residence time are usually determined so that the decomposition of the plastic proceeds sufficiently. The processing temperature and the residence time vary depending on the kind and the amount of the plastic used.
C., preferably 250 to 700.degree. C., more preferably 350 to 500.degree. C., for about 0.5 to 30 minutes, preferably about 1.5 to 15 minutes. At this time, the decomposition behavior differs depending on the type of plastic, but it generally melts, and the main chain of the plastic is broken by catalytic cracking, depolymerized, and gasified, and the decomposed molecules are converted into gas and cracked oil. It is discharged outside and completely separated from metal. The resulting gas or cracked oil can be used as a metal reducing gas or fuel. Next, the metal removed from the cracking furnace removes the attached catalyst by blowing hot air. When the empty volume is large, it is preferable that the metal is compressed to an appropriate size by a press or the like in order to use a melting furnace for melting the recovered metal efficiently.

【0018】なお、溶解炉は製銑分野で使用する炉を使
用することができ、例えばシフト型溶解炉、キュプラ等
が使用できる。溶解炉には熱源としてコークスが装入さ
れるが、さらに前記で分離された分解油およびガスも使
用することが可能である。そのほか、石灰石等をスラグ
温度の低下、流動性改善等の目的で適宜添加される。発
生するスラグの量は高炉法よりも少ないので添加量は高
炉の半分以下でよい。また、運転は製銑に準じた条件で
実施すれば良い。
As the melting furnace, a furnace used in the field of ironmaking can be used, for example, a shift type melting furnace, cupra or the like can be used. The melting furnace is charged with coke as a heat source, but it is also possible to use the cracked oil and gas separated above. In addition, limestone and the like are appropriately added for the purpose of lowering slag temperature, improving fluidity, and the like. Since the amount of slag generated is smaller than in the blast furnace method, the addition amount may be less than half that of the blast furnace. In addition, the operation may be performed under conditions similar to ironmaking.

【0019】[0019]

【実施例】【Example】

実施例1 表1〜3の構成を有する廃自動車の一部を本発明方法で
以下のように処理した。
Example 1 A part of an end-of-life vehicle having the configuration shown in Tables 1 to 3 was treated by the method of the present invention as follows.

【0020】[0020]

【表1】 [Table 1]

【0021】[0021]

【表2】 [Table 2]

【0022】[0022]

【表3】 [Table 3]

【0023】重油の接触分解に用いられるFCC触媒を
加熱窒素でバブリング流動させ、450℃に加熱、充満
させたサンドバス炉にコンベアで連続的に移送された廃
自動車を浸漬し、2分間熱処理を実施した。熱処理後、
残留物を引き上げ、洗浄チャンバーに移送し、密閉下で
熱風を吹き付けて触媒を除去した。なお、この残留物に
付着した炭素量は2.0wt%であった。また、生成物
を回収し分析した結果、廃自動車一台に対し、分解油が
5.15wt%、ガスが1.12wt%の収率であった。
次に得られた残留物をプレス機で体積1/15に圧縮し
た(L1000mm×W1000mm×H500m
m)。この圧縮物を、コークス、石灰石、珪石、蛇紋岩
とともに装入比率1:0.2:0.04:0.02:
0.01になるようにシャフト炉型溶解炉に連続的に装
入し、溶鉱炉の羽口から酸素および水蒸気(1.4/1
混合比(容積))を送風し、同時に回収された分解油を
残留物に対し、40kg/トンの比率で吹き込み、溶銑
と溶滓を排出した。得られた熱処理後の残渣の工業分析
値を表4に、溶解炉操業時の燃料単位比較を表5に、そ
して、溶解炉からの溶銑、溶滓の成分を表6にそれぞれ
示す。
The FCC catalyst used for catalytic cracking of heavy oil is bubbled with heated nitrogen, heated to 450 ° C., immersed in a continuously transported conveyer by a conveyor in a sand bath furnace filled with heat, and heat-treated for 2 minutes. Carried out. After heat treatment,
The residue was taken up, transferred to a washing chamber, and blown with hot air in a sealed state to remove the catalyst. The amount of carbon attached to the residue was 2.0% by weight. Further, as a result of collecting and analyzing the product, the cracked oil and the gas yield were 5.15 wt% and 1.12 wt%, respectively, per one end-of-life vehicle.
Next, the obtained residue was compressed to a volume of 1/15 with a press machine (L1000 mm × W1000 mm × H500 m
m). This compact was charged together with coke, limestone, quartzite and serpentine at a charge ratio of 1: 0.2: 0.04: 0.02:
0.01 was continuously charged into a shaft furnace type melting furnace, and oxygen and steam (1.4 / 1) were introduced through the tuyere of the blast furnace.
(Mixing ratio (volume)) was blown, and at the same time, the recovered cracked oil was blown into the residue at a rate of 40 kg / ton to discharge hot metal and slag. The industrial analysis values of the obtained residue after the heat treatment are shown in Table 4, the fuel unit comparison during the operation of the melting furnace is shown in Table 5, and the components of hot metal and slag from the melting furnace are shown in Table 6.

【0024】実施例2 分解触媒としてZMS−5を用い、温度を390℃とし
た以外は実施例1と同様な方法で廃自動車を処理して残
留物とガス、分解油を得た。分析の結果、残留物には
2.0%の炭素が付着し、廃自動車一台から分解油が
2.94wt%、ガスが3.22wt%の収率で得られ
た。また、得られたガスを水洗した後、溶解炉羽口から
吹き込んだ他は実施例1と同様な条件で溶解炉を操業し
た。結果を表4、5、6に示した。
Example 2 A waste vehicle was treated in the same manner as in Example 1 except that ZMS-5 was used as a cracking catalyst and the temperature was 390 ° C. to obtain a residue, gas and cracked oil. As a result of analysis, 2.0% of carbon was attached to the residue, and cracked oil and gas were obtained at a yield of 2.94 wt% and 3.22 wt% from one end-of-life vehicle. After the obtained gas was washed with water, the melting furnace was operated under the same conditions as in Example 1 except that the gas was blown from the tuyere of the melting furnace. The results are shown in Tables 4, 5, and 6.

【0025】[0025]

【表4】 [Table 4]

【0026】[0026]

【表5】 [Table 5]

【0027】[0027]

【表6】 [Table 6]

【0028】比較例1 流動媒体として0.5mm径のアルミナビーズを用いた
以外は実施例2と同様な方法で廃自動車を処理して残留
物とガス、分解油を得た。分析の結果、残留物には廃自
動車に含まれるプラスチックの約50%が残存し、分解
油が1.8wt%、ガスが0.4wt%の収率であっ
た。残留物の揮発分が8wt%と高いため、煤やタール
の発生が予想されるため溶解炉には供し得なかった。
Comparative Example 1 A waste car was treated in the same manner as in Example 2 except that alumina beads having a diameter of 0.5 mm were used as a fluid medium to obtain a residue, a gas and a cracked oil. As a result of the analysis, about 50% of the plastic contained in the end-of-life vehicle remained in the residue, the yield of cracked oil was 1.8 wt%, and the yield of gas was 0.4 wt%. Since the volatile content of the residue was as high as 8% by weight, soot and tar were expected to be generated, so that the residue could not be used in a melting furnace.

【0029】[0029]

【発明の効果】本発明では、熱分解触媒を流動媒体とす
る熱処理法を採用することにより従来の方法に比べ、金
属複合廃プラスチックから金属および樹脂の回収が容易
となる。
According to the present invention, by employing a heat treatment method using a pyrolysis catalyst as a fluid medium, the recovery of metals and resins from waste metal composite plastics becomes easier as compared with the conventional method.

───────────────────────────────────────────────────── フロントページの続き (72)発明者 有山 達郎 東京都千代田区丸の内一丁目1番2号 日 本鋼管株式会社内 ────────────────────────────────────────────────── ─── Continued on the front page (72) Inventor Tatsuro Ariyama 1-2-1 Marunouchi, Chiyoda-ku, Tokyo Inside Nihon Kokan Co., Ltd.

Claims (2)

【特許請求の範囲】[Claims] 【請求項1】 金属複合プラスチックを、プラスチック
分解触媒を含有する200〜800℃の粉体流動床に浸
漬して該金属複合プラスチック中のプラスチック成分を
分解または溶融して該流動床中へ移行させ、次いで該流
動床を分離することを特徴とする金属複合プラスチック
からの金属および樹脂成分の回収方法
1. A metal composite plastic is immersed in a fluidized bed of powder at 200 to 800 ° C. containing a plastic decomposition catalyst to decompose or melt the plastic component in the metal composite plastic and transfer it into the fluidized bed. And then separating the fluidized bed to recover metal and resin components from a metal composite plastic.
【請求項2】 粉体流動床がプラスチック分解触媒から
なっている請求項1に記載の金属複合プラスチックから
の金属および樹脂成分の回収方法
2. The method for recovering a metal and resin component from a metal composite plastic according to claim 1, wherein the fluidized powder bed comprises a plastic decomposition catalyst.
JP28842297A 1997-10-21 1997-10-21 Method for recovering metal and resin component from metal/plastic composite Pending JPH11116727A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP28842297A JPH11116727A (en) 1997-10-21 1997-10-21 Method for recovering metal and resin component from metal/plastic composite

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP28842297A JPH11116727A (en) 1997-10-21 1997-10-21 Method for recovering metal and resin component from metal/plastic composite

Publications (1)

Publication Number Publication Date
JPH11116727A true JPH11116727A (en) 1999-04-27

Family

ID=17730023

Family Applications (1)

Application Number Title Priority Date Filing Date
JP28842297A Pending JPH11116727A (en) 1997-10-21 1997-10-21 Method for recovering metal and resin component from metal/plastic composite

Country Status (1)

Country Link
JP (1) JPH11116727A (en)

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2012172357A1 (en) * 2011-06-16 2012-12-20 The University Of Nottingham Recycling fibres from polymer composites
JP2014177523A (en) * 2013-03-14 2014-09-25 Shinshu Univ Method and device for treating plastic composite material
US11465084B2 (en) 2020-06-22 2022-10-11 Honeywell Federal Manufacturing & Technologies, Llc Method and system for recovering filler material

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2012172357A1 (en) * 2011-06-16 2012-12-20 The University Of Nottingham Recycling fibres from polymer composites
JP2014177523A (en) * 2013-03-14 2014-09-25 Shinshu Univ Method and device for treating plastic composite material
US11465084B2 (en) 2020-06-22 2022-10-11 Honeywell Federal Manufacturing & Technologies, Llc Method and system for recovering filler material

Similar Documents

Publication Publication Date Title
US11926742B2 (en) Method for preparing carbon black from pyrolysis char of waste tires by molten salt thermal treatment and product thereof
US5198190A (en) Method of recycling hazardous waste
CN1295360C (en) Method of handling spent catalyst
JPH0679252A (en) Method of giving useful product from waste treatment
CN111471866A (en) Method for recycling and harmlessly treating waste aluminum raw material
JP2003039056A (en) Waste treatment method and apparatus utilizing metal refining process
KR20020075785A (en) 2-stage cooling process for synthesis gas
JP2979876B2 (en) Waste treatment method
JPH11116727A (en) Method for recovering metal and resin component from metal/plastic composite
JP2000086807A (en) Apparatus and method for treating oversized plastic- containing waste
JP3346300B2 (en) Method for recovering polymer components from waste plastic
CN114561221A (en) Catalytic pyrolysis gasification method for scrap automobile crushing residue
JP2004216326A (en) Recycling method of car waste
JP4445177B2 (en) Method using gas from settling tank
JP3351294B2 (en) Method and apparatus for treating chlorine-containing synthetic resin
KR100227317B1 (en) Method for recovering reclaimed aluminum material from substances containing metallic aluminum
JP2001098339A (en) Method of producing vanadium alloy iron and vanadium alloy steel
JP3742499B2 (en) Shredder dust treatment method
JPH10259273A (en) Chlorine removal from chlorine-containing polymeric resin
JP3759559B2 (en) Heat medium for treating polymer-containing waste and method for treating polymer-containing waste
JP2003311250A (en) Method for recycling combined waste
JPH11335747A (en) Treatment of waste car and waste house electric appliance
JP2000024616A (en) Heat treatment device for plastic/inorganic material combined waste
JP3764670B2 (en) Waste pyrolysis method
KR100467801B1 (en) Method and Device for high temperature incineration and thermal decomposition of wastes