JPH08112580A - Continuous treatment of combined waste - Google Patents

Continuous treatment of combined waste

Info

Publication number
JPH08112580A
JPH08112580A JP27435394A JP27435394A JPH08112580A JP H08112580 A JPH08112580 A JP H08112580A JP 27435394 A JP27435394 A JP 27435394A JP 27435394 A JP27435394 A JP 27435394A JP H08112580 A JPH08112580 A JP H08112580A
Authority
JP
Japan
Prior art keywords
waste
rotary kiln
metal
content
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.)
Withdrawn
Application number
JP27435394A
Other languages
Japanese (ja)
Inventor
Atsushi Kobayashi
淳志 小林
Ryuichi Abe
隆一 阿部
Takaharu Takeuchi
隆春 武内
Shigeru Mitarai
重 御手洗
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.)
Nippon Steel Corp
Nippon Steel Plant Designing Corp
Original Assignee
Nittetsu Plant Designing Corp
Nippon Steel Corp
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 Nittetsu Plant Designing Corp, Nippon Steel Corp filed Critical Nittetsu Plant Designing Corp
Priority to JP27435394A priority Critical patent/JPH08112580A/en
Publication of JPH08112580A publication Critical patent/JPH08112580A/en
Withdrawn legal-status Critical Current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
    • Y02P10/00Technologies related to metal processing
    • Y02P10/20Recycling
    • 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
    • Y02W30/82Recycling of waste of electrical or electronic equipment [WEEE]

Landscapes

  • Manufacture And Refinement Of Metals (AREA)
  • Processing Of Solid Wastes (AREA)
  • Production Of Liquid Hydrocarbon Mixture For Refining Petroleum (AREA)

Abstract

PURPOSE: To recover a residue increased in metal content and rich in metal and an oil improved in quality from the combined waste consisting of metal and plastics. CONSTITUTION: The combined waste is continuously treated in the following first to third stages. The waste is reduced and thermally decomposed at 200-300 deg.C in a first rotary kiln 1 in the first stage to selectively separate halogen from the plastics in the waste. The waste freed from halogen is transferred to a second rotary kiln 2 arranged in series in the second stage. The waste is reduced and thermally decomposed at 550-650 deg.C in the second rotary kiln 2 in the third stage, and the waste is separated into the decomposed gas, decomposed oil and metal-rich residue which are respectively recovered.

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、金属とプラスチックの
複合廃棄物から金属含有率を向上させた金属リッチ残渣
と品質を向上させた油とを回収する連続処理方法に関す
る。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a continuous treatment method for recovering a metal-rich residue having an improved metal content and an oil having an improved quality from a composite waste of metal and plastic.

【0002】[0002]

【従来の技術】従来、家電廃棄物および自動車廃棄物と
してのシュレッダーダストのような金属とプラスチック
の複合廃棄物の多くは埋立処理されてきた。最近になっ
て複合廃棄物からの資源回収に注目されるようになり、
複合廃棄物中の含有率の高い鉄分やアルミニウム分が磁
選機や渦電流分離機等で回収される例が増えてきたが、
その後は埋立処分されている。また、近年、複合廃棄物
の埋立処理場の減少および金属分の溶出問題が顕在化
し、鉄分、アルミニウム分の回収後焼却処分される例も
増えてきた。
2. Description of the Related Art Conventionally, most of metal and plastic composite wastes such as shredder dust as household electrical appliances waste and automobile waste have been landfilled. Recently, attention has been paid to resource recovery from complex waste,
There is an increasing number of cases where iron and aluminum with high content in composite waste are recovered by magnetic separators and eddy current separators.
After that, it is landfilled. Further, in recent years, the number of landfills for complex wastes has decreased and the problem of elution of metal components has become apparent, and the number of cases of incineration after recovery of iron and aluminum components has increased.

【0003】[0003]

【発明が解決しようとする課題】鉄分およびアルミニウ
ム分が除去された後の複合廃棄物はプラスチック分を5
0%以上含み、また、特に銅分を5〜10%程度含んで
いる。銅分は溶剤回収方法および銅精錬における溶解回
収方法で回収可能であるが、銅の含有率が低いためコス
トがかかり、経済効果がでない。また、複合廃棄物に含
有されるプラスチックの処理についても、前記の燃焼方
法では、プラスチック含有ハロゲン分、すなわち塩素分
およびフッ素分によるハロゲン化水素、すなわち塩化水
素およびフッ化水素の発生がボイラーでの熱回収効率の
低下原因となる。
The composite waste after the iron content and the aluminum content are removed contains 5 parts of the plastic part.
It contains 0% or more, and particularly contains a copper content of about 5 to 10%. The copper content can be recovered by the solvent recovery method and the dissolution recovery method in copper refining, but the copper content is low, so that the cost is high and the economic effect is not achieved. Further, regarding the treatment of plastic contained in the composite waste, in the above combustion method, generation of hydrogen halide due to the plastic-containing halogen content, that is, chlorine content and fluorine content, that is, hydrogen chloride and hydrogen fluoride is generated in the boiler. This causes a decrease in heat recovery efficiency.

【0004】さらに、複合廃棄物を燃焼させ、銅分の回
収を行う例もある。しかしながら、これでは燃焼中に含
有ハロゲン分による含有銅分および他の含有金属分のハ
ロゲン化が生じ、低温度で生じたハロゲン化金属の昇華
が起こり、回収率低下をまねいたり、生じたハロゲン化
金属が銅の製錬工程に悪影響を与えてしまう。
Further, there is an example in which the composite waste is burned to recover the copper content. However, this causes halogenation of the copper content and other metal content due to the halogen content during combustion, which causes the sublimation of the metal halide produced at low temperature, which may lead to a decrease in the recovery rate and the halogenation that has occurred. Metals adversely affect the copper smelting process.

【0005】[0005]

【課題を解決するための手段】本発明は、下記第1〜3
工程からなることを特徴とする主として金属分とプラス
チック分とからなる複合廃棄物の連続処理方法である。
The present invention includes the following first to third aspects.
It is a continuous treatment method of a composite waste consisting mainly of a metal component and a plastic component, which is characterized by comprising steps.

【0006】第1工程:複合廃棄物を第1ロータリーキ
ルンで200℃以上300℃以下で還元熱分解し、複合
廃棄物中のプラスチック分よりハロゲン分を選択除去す
る。
First step: The composite waste is reduced and pyrolyzed in the first rotary kiln at 200 ° C. or higher and 300 ° C. or lower to selectively remove the halogen content from the plastic content in the composite waste.

【0007】第2工程:ハロゲン分を選択除去した複合
廃棄物を直列配置した第2ロータリーキルンに搬送す
る。
Second step: The composite waste from which the halogen content has been selectively removed is conveyed to a second rotary kiln which is arranged in series.

【0008】第3工程:第2ロータリーキルンで複合廃
棄物を550℃以上650℃以下で還元熱分解し、分解
ガス、分解油と金属リッチ残渣とに分離・回収する。
Third step: The composite waste is reduced and thermally decomposed in the second rotary kiln at 550 ° C. or higher and 650 ° C. or lower to separate and recover cracked gas, cracked oil and metal-rich residue.

【0009】[0009]

【作用】第1ロータリーキルンでは、常圧、温度200
〜300℃の還元状態で、対象物滞留時間10分〜2時
間で、複合廃棄物と共に混入可能性の高い水分を除去
し、プラスチック含有ハロゲン分を90%以上分解遊離
させ、ハロゲン化水素として排出する。これにより複合
廃棄物よりハロゲン分を抜き出して回収金属のハロゲン
化を抑制し、金属回収率を向上させる。前記温度範囲以
下ではハロゲン分の分解遊離が遅く、設備が大きくな
り、前記温度範囲以上ではプラスチックの熱分解が促進
され、第2ロータリーキルンで回収される分解ガスおよ
び分解油の収率が低下する。一方、滞留時間は還元温度
ならびに複合廃棄物の種類および形状によるが、ハロゲ
ン分の遊離分解時間を考慮すると10分〜2時間が望ま
しい。
Operation: At the first rotary kiln, normal pressure and temperature of 200
In a reducing state of ~ 300 ° C, water with a high possibility of being mixed together with complex waste is removed with the retention time of the object of 10 minutes to 2 hours, and 90% or more of the plastic-containing halogen content is decomposed and released, and discharged as hydrogen halide. To do. As a result, the halogen content is extracted from the composite waste, the halogenation of the recovered metal is suppressed, and the metal recovery rate is improved. Below the temperature range, the decomposition and liberation of halogen components are slow, and the equipment becomes large, and above the temperature range, the thermal decomposition of plastic is promoted, and the yield of cracked gas and cracked oil recovered in the second rotary kiln decreases. On the other hand, the residence time depends on the reduction temperature and the type and shape of the composite waste, but it is preferably 10 minutes to 2 hours in consideration of the free decomposition time of halogen.

【0010】第1ロータリーキルンに直結した第2ロー
タリーキルンでは、常圧、温度550〜650℃の還元
状態で、対象物滞留時間30分〜2時間で、残存プラス
チックを熱分解し、分解ガス状態で排出する。回収され
た残渣内金属、主に銅は酸化物となることなく回収で
き、金属含有率も向上するため、精錬工程でのメリット
が大きい。また、残渣中に残存する固定炭素が多く、精
錬工程に支障を生じる場合は、残渣を酸化炉へ送入し、
固定炭素を燃焼ガス化させることもできる。この際、一
部の金属は酸化されるが、蒸発・揮散することなく、精
錬工程での支障は少ない。
In the second rotary kiln, which is directly connected to the first rotary kiln, the residual plastic is thermally decomposed and discharged in a decomposed gas state in a reducing state at atmospheric pressure and a temperature of 550 to 650 ° C. for a residence time of 30 minutes to 2 hours. To do. The metal in the recovered residue, mainly copper, can be recovered without becoming an oxide, and the metal content is also improved, which is a great advantage in the refining process. Also, if there is a large amount of fixed carbon remaining in the residue and it interferes with the refining process, send the residue to an oxidation furnace,
It is also possible to convert fixed carbon into combustion gas. At this time, some of the metals are oxidized, but they do not evaporate or volatilize, and there are few obstacles in the refining process.

【0011】前記温度範囲以下ではプラスチックの熱分
解に時間がかかり、設備が大きくなり、前記温度範囲以
上では金属分の溶融および昇華が生じ、キルン内閉塞を
生じる可能性が高くなる。また、滞留時間は還元温度な
らびに複合廃棄物の種類および形状によるが、プラスチ
ック分の分解時間を考慮すると30分〜2時間が望まし
い。
If the temperature is lower than the above range, the thermal decomposition of the plastic takes time and the equipment becomes large, and if the temperature is above the above range, the melting and sublimation of the metal component occurs and the possibility of clogging in the kiln increases. Although the residence time depends on the reduction temperature and the type and shape of the composite waste, it is preferably 30 minutes to 2 hours in consideration of the decomposition time of the plastic component.

【0012】熱分解で発生した分解ガスおよび分解油は
冷却され、分解ガス、分解油として貯蔵可能で、しかも
第1ロータリーキルンでハロゲン分を除去しているため
エネルギーとしての品質も高く、他の設備のエネルギー
源として使用できるし、本発明を実施するための設備で
使用することも可能である。
The cracked gas and cracked oil generated by thermal decomposition can be cooled and stored as cracked gas and cracked oil, and since the halogen content is removed by the first rotary kiln, the energy quality is high and other equipment Can be used as an energy source of the present invention, and can also be used in equipment for carrying out the present invention.

【0013】[0013]

【実施例】本発明の実施例を図1を用いて以下に説明す
る。
EXAMPLE An example of the present invention will be described below with reference to FIG.

【0014】第1および第2ロータリーキルンとして、
外部加熱方式のロータリーキルンの2段直列型を使用し
た。
As the first and second rotary kilns,
A two-stage series type of external heating type rotary kiln was used.

【0015】第1ロータリーキルン1は原料ホッパー3
を有し、原料ホッパー3と第1ロータリーキルン1との
間には、シール性を向上させるため2段のゲート弁4を
有する。原料を第1ロータリーキルン1に送り込む場
合、上部ゲート弁を開き、原料をゲート弁間に送り、上
部ゲート弁を閉じ、下部ゲート弁を開き、その下部プッ
シャー部に複合廃棄物を送入し、その後下部ゲート弁を
閉じる。複合廃棄物はプッシャー5で第1ロータリーキ
ルン1に送入する。
The first rotary kiln 1 is a raw material hopper 3
In addition, a two-stage gate valve 4 is provided between the raw material hopper 3 and the first rotary kiln 1 to improve the sealing performance. When the raw material is fed into the first rotary kiln 1, the upper gate valve is opened, the raw material is fed between the gate valves, the upper gate valve is closed, the lower gate valve is opened, and the composite waste is fed into the lower pusher portion, and thereafter. Close the lower gate valve. The composite waste is sent to the first rotary kiln 1 by the pusher 5.

【0016】第1ロータリーキルン1は内筒と外筒を有
し、外筒内部かつ内筒外部で燃料を燃焼し、内筒内部の
複合廃棄物を200〜300℃の温度で還元分解する。
外筒は固定で、内筒が回転する。第1ロータリーキルン
1で複合廃棄物中のプラスチック内ハロゲン分を遊離分
解し、塩化水素およびフッ化水素の酸性ガスとして排ガ
ス処理する。
The first rotary kiln 1 has an inner cylinder and an outer cylinder, burns fuel inside the outer cylinder and outside the inner cylinder, and reduces and decomposes the composite waste inside the inner cylinder at a temperature of 200 to 300 ° C.
The outer cylinder is fixed and the inner cylinder rotates. In the first rotary kiln 1, the halogen component in the plastic in the composite waste is liberated and decomposed, and the exhaust gas is treated as an acidic gas of hydrogen chloride and hydrogen fluoride.

【0017】第1ロータリーキルン1排出残渣内には多
くの炭素、水素、酸素分を含有しており、これらはその
まま直結されている第2ロータリーキルン2に送入す
る。第1ロータリーキルン1と第2ロータリーキルン2
との間のシール6はゲート弁を有しても有しなくてもよ
い。送入にプッシャー方式を使用する場合にはゲート弁
を要し、ルーダー方式を使用する場合には送入物本体で
シールするためゲート弁は必要ない。
The exhaust residue of the first rotary kiln 1 contains a large amount of carbon, hydrogen, and oxygen, and these are directly sent to the second rotary kiln 2 which is directly connected. 1st rotary kiln 1 and 2nd rotary kiln 2
The seal 6 between and may or may not have a gate valve. A gate valve is required when using the pusher method for delivery, and a gate valve is not required when using the ruder method because the feed is sealed by the body.

【0018】第2ロータリーキルン2は第1ロータリー
キルン1と同じ外部加熱方式で、外部固定、内部回転型
である。加熱温度は550〜650℃で、分解ガスはハ
ロゲン原子が除去された品質の高い燃料源となる。分解
残渣の抜き出しも第1ロータリーキルン1と第2ロータ
リーキルン2との間のシールと同じである。
The second rotary kiln 2 has the same external heating system as the first rotary kiln 1 and is of the external fixed type and the internal rotary type. The heating temperature is 550 to 650 ° C., and the cracked gas becomes a high-quality fuel source from which halogen atoms have been removed. Extraction of the decomposition residue is the same as the seal between the first rotary kiln 1 and the second rotary kiln 2.

【0019】[0019]

【発明の効果】本発明では、主として金属分とプラスチ
ック分とからなる複合廃棄物より、第1ロータリーキル
ンで選択的にハロゲン分を排出させるので、第2ロータ
リーキルンでハロゲン分を含まない品質の高い分解ガ
ス、分解油、および金属リッチ残渣を回収することが可
能である。
According to the present invention, since the halogen content is selectively discharged from the composite waste mainly consisting of the metal content and the plastic content in the first rotary kiln, the second rotary kiln does not contain halogen content and has a high quality decomposition. It is possible to recover gas, cracked oil, and metal rich residues.

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

【図1】本発明を実施するための装置の例を示す図であ
る。
FIG. 1 shows an example of a device for implementing the invention.

【符号の説明】[Explanation of symbols]

1 第1ロータリーキルン 2 第2ロータリーキルン 3 原料ホッパー 4 ゲート弁 5 プッシャー 6 シール 7 金属残渣抜き出し 1 1st rotary kiln 2 2nd rotary kiln 3 Raw material hopper 4 Gate valve 5 Pusher 6 Seal 7 Metal residue extraction

フロントページの続き (51)Int.Cl.6 識別記号 庁内整理番号 FI 技術表示箇所 C10J 3/00 ZAB A B09B 3/00 302 A (72)発明者 武内 隆春 北九州市戸畑区大字中原46−59 新日本製 鐵株式会社機械・プラント事業部内 (72)発明者 御手洗 重 北九州市戸畑区大字中原46−59 日鐵プラ ント設計株式会社内Continuation of front page (51) Int.Cl. 6 Identification number Office reference number FI Technical indication location C10J 3/00 ZAB A B09B 3/00 302 A (72) Inventor Takaharu Takeuchi 46-59 Nakahara, Tobata-ku, Kitakyushu Nippon Steel Co., Ltd., Machinery & Plant Division (72) Inventor Shigeru Mitarai 46-59 Nakahara, Tobata-ku, Kitakyushu City Inside Nippon Steel Plant Design Co., Ltd.

Claims (1)

【特許請求の範囲】[Claims] 【請求項1】 下記第1〜3工程からなることを特徴と
する主として金属分とプラスチック分とからなる複合廃
棄物の連続処理方法。 第1工程:複合廃棄物を第1ロータリーキルンで200
℃以上300℃以下で還元熱分解し、複合廃棄物中のプ
ラスチック分よりハロゲン分を選択除去する。 第2工程:ハロゲン分を選択除去した複合廃棄物を直列
配置した第2ロータリーキルンに搬送する。 第3工程:第2ロータリーキルンで複合廃棄物を550
℃以上650℃以下で還元熱分解し、分解ガス、分解油
と金属リッチ残渣とに分離・回収する。
1. A continuous treatment method for a composite waste consisting mainly of a metal component and a plastic component, which comprises the following first to third steps. 1st process: Combined waste is 200 in 1st rotary kiln
It undergoes reductive thermal decomposition at temperatures between ℃ and 300 ℃ and selectively removes halogen from the plastic in the composite waste. Second step: The composite waste from which the halogen content is selectively removed is conveyed to the second rotary kiln which is arranged in series. 3rd step: 550 compound waste in 2nd rotary kiln
It undergoes reductive thermal decomposition at temperatures above 650 ° C and is separated and recovered into decomposed gas, decomposed oil and metal-rich residue.
JP27435394A 1994-10-14 1994-10-14 Continuous treatment of combined waste Withdrawn JPH08112580A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP27435394A JPH08112580A (en) 1994-10-14 1994-10-14 Continuous treatment of combined waste

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP27435394A JPH08112580A (en) 1994-10-14 1994-10-14 Continuous treatment of combined waste

Publications (1)

Publication Number Publication Date
JPH08112580A true JPH08112580A (en) 1996-05-07

Family

ID=17540480

Family Applications (1)

Application Number Title Priority Date Filing Date
JP27435394A Withdrawn JPH08112580A (en) 1994-10-14 1994-10-14 Continuous treatment of combined waste

Country Status (1)

Country Link
JP (1) JPH08112580A (en)

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JPH1161146A (en) * 1997-08-08 1999-03-05 Takeshi Kuroki Apparatus for continuously converting waste plastic to oil
JPH11315162A (en) * 1998-03-02 1999-11-16 Toshiba Corp Heat treatment and heat treating system
KR100704307B1 (en) * 2005-03-10 2007-04-06 백성혁 Waste synthetic resin recycling oil extraction an apparatus
JP2007238858A (en) * 2006-03-10 2007-09-20 Ihi Corp Method and apparatus for pyrolysis gasification of waste
JP2008528708A (en) * 2005-01-18 2008-07-31 エンクエスト パワー コーポレーション Method for steam reforming of carbonaceous feedstock
JP2011067800A (en) * 2009-09-28 2011-04-07 Ihi Corp Method and apparatus for pyrolyzing waste
KR20160080937A (en) * 2014-12-30 2016-07-08 울산대학교 산학협력단 Method and device for regenerating fuel oil from plastics and vinyls wastes
JP2019507234A (en) * 2015-12-31 2019-03-14 シーエイチゼット テクノロジーズ,リミティド ライアビリティ カンパニー Multi-stage pyrolysis method for safe and efficient conversion of waste sources
JP2019507682A (en) * 2015-12-31 2019-03-22 シーエイチゼット テクノロジーズ,リミティド ライアビリティ カンパニー Multi-step pyrolysis method for safe and efficient conversion of electronic waste materials
JP2023507514A (en) * 2019-12-20 2023-02-22 プラスティック・エナジー・リミテッド Method and system for pyrolyzing plastic materials

Cited By (16)

* Cited by examiner, † Cited by third party
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