JPH0523328B2 - - Google Patents

Info

Publication number
JPH0523328B2
JPH0523328B2 JP18370285A JP18370285A JPH0523328B2 JP H0523328 B2 JPH0523328 B2 JP H0523328B2 JP 18370285 A JP18370285 A JP 18370285A JP 18370285 A JP18370285 A JP 18370285A JP H0523328 B2 JPH0523328 B2 JP H0523328B2
Authority
JP
Japan
Prior art keywords
gas
combustion
primary reaction
reaction chamber
metal
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
JP18370285A
Other languages
Japanese (ja)
Other versions
JPS6246117A (en
Inventor
Satoru Yoshinaka
Seiji Matsuda
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.)
Individual
Original Assignee
Individual
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 Individual filed Critical Individual
Priority to JP60183702A priority Critical patent/JPS6246117A/en
Publication of JPS6246117A publication Critical patent/JPS6246117A/en
Publication of JPH0523328B2 publication Critical patent/JPH0523328B2/ja
Granted legal-status Critical Current

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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

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  • Incineration Of Waste (AREA)
  • Gasification And Melting Of Waste (AREA)
  • Processing Of Solid Wastes (AREA)
  • Manufacture And Refinement Of Metals (AREA)

Description

【発明の詳細な説明】 [産業上の利用分野] 本発明は、少なくとも固形可燃性有機物質と金
属とを混合状態で含む被処理物から金属を回収す
るための方法及び装置に関する。
DETAILED DESCRIPTION OF THE INVENTION [Field of Industrial Application] The present invention relates to a method and apparatus for recovering metals from a workpiece containing at least a solid combustible organic substance and metals in a mixed state.

[従来の技術及び解決しようとする問題点] 多くの廃却電線はプラスチツク類で絶縁被覆さ
れ、鉄鋼原料としてのスクラツプも、プラスチツ
ク類で被覆されている物が増加の一途をたどり、
例えば廃却乗用車など全重量の1/4〜1/5の割合を
示すに至つている現状であり、加うるに、近時、
プラスチツク類の基盤上に金・白金等を接点部材
として電子部品が配着されたものの廃棄品が増大
しつつある。
[Prior art and problems to be solved] Many discarded electric wires are insulated with plastics, and the number of scraps used as raw materials for steel that are coated with plastics is increasing.
For example, the current situation is that it accounts for 1/4 to 1/5 of the total weight of scrapped passenger cars, and in addition, recently,
The amount of discarded electronic components that are made of plastic substrates with gold, platinum, etc. as contact members is increasing.

このような固形可燃性有機物質と金属とを混合
状態で含む被処理物から金、白金、銀、銅、鉄な
どの金属を回収する場合、焼却炉を利用する回収
手段よりも、むしろ機械的な削り取り・抜き取り
または、まれに極低温処理後の粉砕分離等の回収
手段がとられているが、コスト高の上、分離後の
プラスチツク類などは、終局的に埋立・焼却等の
処分を必要とするなど、問題点が多い。
When recovering metals such as gold, platinum, silver, copper, and iron from materials that contain a mixture of solid combustible organic substances and metals, mechanical recovery methods are used rather than recovery methods that use incinerators. Collection methods such as scraping and extraction or, in rare cases, pulverization separation after cryogenic treatment are taken, but in addition to the high cost, the plastics after separation must ultimately be disposed of by landfilling or incineration. There are many problems, such as:

勿論、焼却炉で焼却分離されることもあるが、
その場合は、過焼に依る金属の変質や金属の酸化
等のため、その回収品の価値の下落及び収率低下
を招来することとなる。また、焼却炉の一次燃焼
室で可燃性物質の完全燃焼化をすることができ
ず、その有煙廃ガスを二次燃焼室、三次燃焼室に
おける一般燃料を用いたバーナでアフターバーニ
ングする方式の焼却炉が多く、而も該二次燃焼
室、三次燃焼室のアフターバーニングはもとよ
り、一次燃焼室においても、一般燃料を用いてバ
ーナで助燃しなければならない場合が多い。その
ため何れにしても高コスト化を免れ得ず、更に、
上述の燃焼・焼却を行つても、煤塵発生が多量
で、集塵装置が不可欠の付帯設備となり、装置の
コスト及び操作コストの高騰を招来する所以とな
る。
Of course, it may be incinerated and separated in an incinerator, but
In that case, the quality of the metal changes due to overfiring, the oxidation of the metal, etc., resulting in a decrease in the value of the recovered product and a decrease in yield. In addition, it is not possible to completely burn combustible materials in the primary combustion chamber of an incinerator, and the method of afterburning the smoky waste gas with burners using general fuel in the secondary and tertiary combustion chambers has been proposed. There are many incinerators, and in addition to afterburning in the secondary and tertiary combustion chambers, it is often necessary to perform auxiliary combustion with a burner using general fuel in the primary combustion chamber as well. Therefore, in any case, high costs cannot be avoided, and furthermore,
Even when the above-mentioned combustion and incineration are carried out, a large amount of soot and dust is generated, and a dust collector becomes an indispensable auxiliary equipment, which causes a rise in the cost of the device and the operating cost.

本発明は、従来技術に存した上記のような問題
点に鑑み行われたものであつて、その目的とする
ところは、少なくとも固形可燃性有機物質と金属
とを混合状態で含む被処理物から、低コストでも
つて、品質の良い状態の有価金属を高い回収率で
回収し、排ガス熱を効率的に利用すると共に排ガ
スを清浄化することができるガス化燃焼による金
属回収方法及び金属回収用ガス化燃焼装置を提供
することにある。
The present invention has been made in view of the above-mentioned problems existing in the prior art, and its purpose is to remove at least a material to be treated containing a mixed state of a solid combustible organic substance and a metal. A metal recovery method and gas for metal recovery using gasification combustion that can recover valuable metals in good quality at a high recovery rate at low cost, efficiently utilize exhaust gas heat, and purify exhaust gas. The purpose of the present invention is to provide a chemical combustion device.

[問題点を解決するための手段] 上記目的を達成するために、本発明のガス化燃
焼による金属回収方法は、 少なくとも固形可燃性有機物質と金属とを混合
状態で含む被処理物から金属を回収する方法であ
つて、 一次反応室に前記被処理物を収容させて着火し
た後、 その被処理物中の有機物質に不完全燃焼及び熱
分解が生ずるように一次反応室に空気を制御送入
することによつて可燃性ガスを発生させ、 不完全燃焼及び熱分解により被処理物中の有機
物質から生成した炭分との間で水性ガス反応が生
ずるように一次反応室に水蒸気を制御送入するこ
とによつて、水性ガスを発生させると共に被処理
物中における回収すべき金属の品質劣化を防止し
得る程度に高温化を抑制し、 一次反応室において有機物質の不完全燃焼及び
熱分解により発生した可燃性ガス及び水性ガス反
応により発生した水性ガスをガス燃焼室に導くと
共にそのガス燃焼室に空気又は空気及び水蒸気を
送入し、 一般燃料による助燃バーナによつて一時的に助
燃することにより前記可燃性ガス及び水性ガスの
継続的自燃を行わせるものとしている。
[Means for Solving the Problems] In order to achieve the above object, the metal recovery method by gasification combustion of the present invention collects metals from a material to be treated containing at least a solid combustible organic substance and a metal in a mixed state. A recovery method, which comprises placing the material to be treated in a primary reaction chamber, igniting it, and then controllingly sending air into the primary reaction chamber so as to cause incomplete combustion and thermal decomposition of the organic substances in the material to be treated. The water vapor is controlled in the primary reaction chamber so that a flammable gas is generated by entering the water vapor, and a water gas reaction occurs with the carbon produced from the organic substances in the material to be treated through incomplete combustion and thermal decomposition. By supplying water gas, water gas is generated, and the temperature rise is suppressed to the extent that deterioration of the quality of the metal to be recovered in the material to be treated can be prevented. The flammable gas generated by decomposition and the water gas generated by the water gas reaction are guided into a gas combustion chamber, and air or air and water vapor are introduced into the gas combustion chamber, and temporarily auxiliary combustion is performed using an auxiliary combustion burner using general fuel. By doing so, continuous self-combustion of the flammable gas and water gas is performed.

また本発明の金属回収用ガス化燃焼装置は、 少なくとも固形可燃性有機物質と金属とを混合
状態で含む被処理物から金属を回収するための装
置であつて、 前記被処理物を容入する一次反応室と、 被処理物中の有機物質に不完全燃焼及び熱分解
が生じて可燃性ガスが発生するように一次反応室
に空気を制御送入するための空気制御送入手段
と、 不完全燃焼及び熱分解により被処理物中の有機
物質から生成した炭分との間で水性ガス反応が生
じて水性ガスを発生させると共に被処理物中にお
ける回収すべき金属の品質劣化を防止し得る程度
に高温化が抑制されるように一次反応室に水蒸気
を制御送入するための水蒸気制御送入手段と、 一次反応室において有機物質の不完全燃焼及び
熱分解により発生した可燃性ガス及び水性ガス反
応により発生した水性ガスが導かれるガス燃焼室
と、 ガス燃焼室に空気又は空気及び水蒸気を送入す
るための送入手段と、 一時的に助燃することにより前記可燃性ガス及
び水性ガスの継続的自燃を行わせるための一般燃
料による助燃バーナとを備えるものとしている。
Further, the gasification combustion apparatus for metal recovery of the present invention is an apparatus for recovering metals from a workpiece containing at least a solid combustible organic substance and a metal in a mixed state, and contains the workpiece. a primary reaction chamber; an air control supply means for controllingly supplying air to the primary reaction chamber to cause incomplete combustion and thermal decomposition of the organic material in the material to be treated to generate flammable gas; A water gas reaction occurs between the carbon content generated from the organic substances in the material to be treated through complete combustion and thermal decomposition, generating water gas and preventing quality deterioration of the metals to be recovered in the material to be treated. a steam control supply means for controlling and supplying steam to the primary reaction chamber so as to suppress the temperature increase to a certain degree; a gas combustion chamber to which water gas generated by the gas reaction is introduced; a feeding means for feeding air or air and water vapor into the gas combustion chamber; It is equipped with an auxiliary combustion burner using general fuel for continuous self-combustion.

[作用] 一次反応室に前記被処理物を収容させて着火し
た後、その被処理物中の有機物質に不完全燃焼及
び熱分解が生ずるように一次反応室に空気を制御
送入すると、不完全燃焼により有機物質中の炭素
分は二酸化炭素化が抑制されて一酸化炭素化傾向
を増大し、可燃性成分が豊富となる。そして、有
機物質の不完全燃焼はその反応熱による有機物質
の熱分解を促し、その結果、炭化水素系ガス及び
水素ガス等を生成する。
[Function] After the material to be treated is stored in the primary reaction chamber and ignited, air is controlled to be fed into the primary reaction chamber so that incomplete combustion and thermal decomposition of the organic substances in the material to be treated occur. Complete combustion suppresses the conversion of carbon content in organic substances into carbon dioxide, increases the tendency to convert them into carbon monoxide, and enriches combustible components. Incomplete combustion of the organic substance promotes thermal decomposition of the organic substance due to the reaction heat, and as a result, hydrocarbon gas, hydrogen gas, etc. are generated.

有機物質の不完全燃焼及び熱分解は、一方にお
いては炭化を進行させ、生成炭分がおき火状態と
なるが、その炭分との間で水性ガス反応が生ずる
ように一次反応室に水蒸気を制御送入することに
よつて、炭分を消化しつつ水性ガスを発生させる
ことができると共に、水性ガス反応が吸熱反応で
あることから、被処理物中における回収すべき金
属の品質劣化を防止し得る程度に高温化を抑制す
ることが可能である。而も、サーマルNOxの生
成をも半減させる。
Incomplete combustion and thermal decomposition of organic substances, on the one hand, promotes carbonization, and the resulting coal becomes a kindling state. By controlling the feeding, it is possible to generate water gas while digesting the charcoal, and since the water gas reaction is an endothermic reaction, it prevents quality deterioration of the metals to be recovered in the material to be treated. It is possible to suppress the increase in temperature to the extent possible. Moreover, it also halves the generation of thermal NO x .

更に、上記のような不完全燃焼による一酸化炭
素ガス、熱分解による水素ガス並びに水性ガス反
応による水素ガス及び一酸化炭素ガスは還元作用
を発揮するので、一次反応室において、被処理物
中の金属の酸化が防がれる。
Furthermore, carbon monoxide gas due to incomplete combustion, hydrogen gas due to thermal decomposition, and hydrogen gas and carbon monoxide gas due to water gas reaction exhibit a reducing effect, so in the primary reaction chamber, the Metal oxidation is prevented.

以上のようにして一次反応室において有機物質
の不完全燃焼及び熱分解により発生した可燃性ガ
ス並びに水性ガス反応により発生した水性ガスを
ガス燃焼室に導くと共に、そのガス燃焼室に空気
又は空気及び水蒸気を送入し、一般燃料による助
燃バーナによつて一時的に助燃することにより、
前記可燃性ガス及び水性ガスの継続的自燃を行わ
せることができる。
As described above, flammable gas generated by incomplete combustion and thermal decomposition of organic substances in the primary reaction chamber and water gas generated by water gas reaction are introduced into the gas combustion chamber, and air or air and By introducing steam and temporarily auxiliary combustion using an auxiliary combustion burner using general fuel,
Continuous self-combustion of the flammable gas and water gas can be performed.

そして、一次反応室において、空気の制御送入
による有機物質の不完全燃焼と水蒸気の制御送入
による水性ガス反応とにより、一酸化炭素ガス、
炭化水素系ガス及び水素ガス等の可燃性のガスの
生成が非常に効率的に行われることと、それらの
ガスが一次反応室において十分に予熱されている
こととが相まつて、ガス燃焼室において理想的な
完全燃焼状態が継続的に得られ、排ガス中のダス
ト濃度が極めて低くなる。
Then, in the primary reaction chamber, carbon monoxide gas,
The combination of the highly efficient production of combustible gases such as hydrocarbon gases and hydrogen gas, and the fact that these gases are sufficiently preheated in the primary reaction chamber, results in Ideal complete combustion conditions are continuously achieved, and the dust concentration in the exhaust gas is extremely low.

[実施例] 本発明の実施例を、図面を参照しつつ説明す
る。
[Example] An example of the present invention will be described with reference to the drawings.

1は、少なくとも固形可燃性有機物質と金属と
を混合状態で含む被処理物を収容する一次反応室
である。被処理物としては、具体的には、被覆電
線、回路基板、それらを含む電気または電子機
器、プラスチツクと金属とが一体をなす各種の機
器またはその部分品、或は、これらと他の可燃性
有機物質または不燃性物質等との混合物などを例
示することができる。
Reference numeral 1 denotes a primary reaction chamber that accommodates a processed material containing at least a solid combustible organic substance and a metal in a mixed state. Specifically, the objects to be treated include coated electric wires, circuit boards, electrical or electronic equipment containing them, various types of equipment or parts thereof in which plastic and metal are integrated, or these and other combustible materials. Examples include mixtures with organic substances or nonflammable substances.

2は、制御弁3及び空気供給管4を介して一次
反応室底床部5に連通する供空機である。制御弁
3の作動により、一次反応室底床部5に開口する
多数の空気噴出口6……6を介して行われる一次
反応室1腔部への空気送入量が制御され、一次反
応室1に収容された被処理物中の有機物質に、不
完全燃焼と、その不完全燃焼熱による熱分解とが
生ずる。
2 is an air supply machine that communicates with the bottom floor 5 of the primary reaction chamber via a control valve 3 and an air supply pipe 4. By operating the control valve 3, the amount of air fed into the first cavity of the primary reaction chamber through the numerous air jet ports 6...6 opened in the bottom floor 5 of the primary reaction chamber is controlled. Incomplete combustion and thermal decomposition due to the heat of the incomplete combustion occur in the organic substances contained in the material to be treated stored in the container.

7は、空気供給管4途次に連通する水蒸気供給
管である。水蒸気ボイラー(図示を略す。)で生
成した水蒸気は、一次反応室1内の生成炭分との
間に水性ガス反応を生じさせて水性ガスを発生さ
せると共に回収すべき金属の品質劣化を防止し得
る程度に高温化を抑制するべく、空気供給管4中
にて送給空気と混合して一次反応室1に制御送入
されるものである。
7 is a water vapor supply pipe that communicates with the air supply pipe 4 . The steam generated in the steam boiler (not shown) causes a water gas reaction with the generated coal in the primary reaction chamber 1 to generate water gas and prevent quality deterioration of the metal to be recovered. In order to suppress the rise in temperature to the extent that it is possible to obtain the desired temperature, the mixture is mixed with feed air in the air supply pipe 4 and controlled to be fed into the primary reaction chamber 1.

8は、可燃性ガス吹出口9を介して、一次反応
室1内生成の可燃性のガスが送給されるガス燃焼
室であつて、供空機10のみ又は供空機10及び
水蒸気供給管11の両者よりそれぞれ送給される
空気又は空気及び水蒸気の混合物の存在下に、一
般燃料による助燃バーナ12の一時的助燃によ
り、一次反応室1より送給される可燃性ガスが継
続的自燃し得る如く構成されている。
8 is a gas combustion chamber to which combustible gas generated in the primary reaction chamber 1 is fed via a flammable gas outlet 9, and includes only the air supply device 10 or the air supply device 10 and the steam supply pipe. In the presence of air or a mixture of air and water vapor supplied from both of the primary reaction chamber 1 and 11, the combustible gas supplied from the primary reaction chamber 1 continuously self-combusts due to temporary auxiliary combustion of the auxiliary combustion burner 12 using general fuel. It is structured in such a way that it can be obtained.

以上のような装置において、まず一次反応室1
内に固形可燃性物質又は該固形可燃性物質を含む
金属廃棄物を天蓋13より収容させ、当該一次反
応室1正面配設の回収扉14を閉扉し、引続い
て、一般燃料、就中重油を用いる助燃バーナ12
を点火始動して、ガス燃焼室8内に燃焼火炎をつ
くる。
In the above-described apparatus, first, the primary reaction chamber 1
A solid combustible substance or metal waste containing the solid combustible substance is contained in the chamber through the canopy 13, the recovery door 14 provided in front of the primary reaction chamber 1 is closed, and then general fuel, especially heavy oil An auxiliary combustion burner 12 using
ignition is started to create a combustion flame in the gas combustion chamber 8.

その火炎は、ガス燃焼室8の内壁を加熱しつつ
廃ガスとして排ガス口15を介して大気中に放出
される。その排ガス口15は、装置の設備場所の
環境条件に対応して、適宜煙突(図示を略す。)
と接続すれば、好都合である。
The flame heats the inner wall of the gas combustion chamber 8 and is discharged into the atmosphere through the exhaust gas port 15 as waste gas. The exhaust gas port 15 may be connected to a chimney (not shown) as appropriate depending on the environmental conditions of the equipment location.
It is convenient if you connect it with

前記助燃バーナ12の点火始動後、直ちに供空
機10を始動して、空気供給管16を介してガス
燃焼室8に空気を送給し、送給せられた空気は助
燃バーナ12により生成される廃ガスと共に、排
ガス口15を介して大気中に放出されることとな
る。
Immediately after the ignition of the auxiliary burner 12 is started, the air supply device 10 is started to supply air to the gas combustion chamber 8 via the air supply pipe 16, and the supplied air is generated by the auxiliary burner 12. The exhaust gas is discharged into the atmosphere through the exhaust gas port 15 together with the waste gas.

次に、一次反応室1内に貯溜される被処理物中
の一次反応室底床部5近傍に点火し、回収扉14
を閉扉し、閉扉後直ちに供空機2を始動して、制
御弁3……3を介して、制御された空気量を空気
吹出口6……6より一次反応室底床部5に送給す
る。
Next, the vicinity of the bottom floor 5 of the primary reaction chamber in the material to be treated stored in the primary reaction chamber 1 is ignited, and the collection door 14 is ignited.
Immediately after the door is closed, the air supply machine 2 is started, and a controlled amount of air is sent to the bottom floor 5 of the primary reaction chamber from the air outlet 6...6 via the control valve 3...3. do.

かくして、一次反応室1内の可燃性有機物質の
燃焼は、制御弁3……3による送入空気量の制御
により不完全燃焼となり、これによつて、可燃性
有機物質中の炭素分は二酸化炭素化が抑制されて
一酸化炭素(CO)化傾向を増大し、可燃性成分
が豊富となる。
In this way, the combustion of the combustible organic substance in the primary reaction chamber 1 becomes incomplete combustion by controlling the amount of air introduced by the control valves 3...3, and as a result, the carbon content in the combustible organic substance becomes Carbonization is suppressed, increasing the tendency to convert to carbon monoxide (CO), and flammable components become abundant.

更に、前記の可燃性有機物質の不完全燃焼は、
その反応熱による固形可燃性物質の熱分解を促
し、その結果、炭化水素系ガス(CnHo)及び水
素(H2)等を生成する。
Furthermore, the incomplete combustion of the combustible organic substances mentioned above
The heat of reaction promotes thermal decomposition of the solid combustible material, and as a result, hydrocarbon gas (C n H o ), hydrogen (H 2 ), etc. are generated.

ところで、前述の一次反応室1における可燃性
有機物質の不完全燃焼及び熱分解は、一方におい
ては、炭化を進行せしめ、ここに供空機2による
空気供給の続行に伴うおき火状態における高温を
招来し、被処理物中の金属、例えば銅・鉄等の品
質を劣化させたり溶融させて回収不能とするとい
う問題点がある。
By the way, the incomplete combustion and thermal decomposition of the combustible organic substance in the primary reaction chamber 1 described above, on the one hand, promotes carbonization and increases the high temperature in the bonfire state due to the continuation of air supply by the air supplier 2. However, there is a problem in that the quality of metals in the object to be treated, such as copper and iron, deteriorates or melts, making them unrecoverable.

ところがこの装置においては、水蒸気が水蒸気
供給管7を介して空気供給管4中の空気に混入さ
れて一次反応室底床部5に制御送入せられるの
で、生成炭分の下記水性ガス反応が起こり、水性
ガスたる一酸化炭素(CO)と水素(H2)を生成
させる。
However, in this device, water vapor is mixed with the air in the air supply pipe 4 via the steam supply pipe 7 and is controlled to be sent to the bottom floor 5 of the primary reaction chamber, so that the following water gas reaction of the produced coal is carried out. This occurs, producing the water gases carbon monoxide (CO) and hydrogen (H 2 ).

C+H2O→CO+H2 如上の水性ガス反応は、公知の如く吸熱反応で
あり、而も炭素(C)が一酸化炭素(CO)ガス
となつて消化される反応である。
C+H 2 O→CO+H 2 The above water gas reaction is, as is well known, an endothermic reaction in which carbon (C) is digested into carbon monoxide (CO) gas.

従つて、この装置においては、前記の空気及び
水蒸気の送給量の調整により、一次反応室1内の
温度が容易且つ自在に調整されて金属の過焼を防
止し得、且つ炭素(C)の効果的消化を行い得る
こととなる。而も、不完全燃焼による一酸化炭素
ガス、熱分解による水素ガス並びに水性ガス反応
による水素ガス及び一酸化炭素ガスは還元作用を
発揮するので、一次反応室1において、回収すべ
き有価金属の酸化が防がれる。
Therefore, in this device, the temperature inside the primary reaction chamber 1 can be easily and freely adjusted by adjusting the amount of air and water vapor to be fed, thereby preventing over-firing of the metal, and the carbon (C) can be effectively digested. However, since carbon monoxide gas due to incomplete combustion, hydrogen gas due to thermal decomposition, and hydrogen gas and carbon monoxide gas due to water gas reaction exhibit a reducing effect, the oxidation of valuable metals to be recovered is performed in the primary reaction chamber 1. is prevented.

以上のようにして可燃性有機物質の不完全燃
焼、熱分解及び水性ガス反応により効率的に発生
した一酸化炭素ガス、炭化水素系ガス及び水素ガ
ス等の燃焼性の良いガスが、一次反応室1にて十
分予熱された状態でガス燃焼室8に送られて、理
想的な完全燃焼状態が継続的に得られ、排ガス中
のダスト濃度が極めて低くなると共に、排ガス熱
を効率的に利用することができる。
As described above, highly combustible gases such as carbon monoxide gas, hydrocarbon gas, and hydrogen gas efficiently generated through incomplete combustion, thermal decomposition, and water gas reaction of combustible organic substances are transferred to the primary reaction chamber. The gas is sent to the gas combustion chamber 8 in a state that has been sufficiently preheated in step 1, so that ideal complete combustion conditions are continuously obtained, the dust concentration in the exhaust gas is extremely low, and exhaust gas heat is efficiently utilized. be able to.

なお、一次反応室1よりガス燃焼室8へ可燃性
ガスを送給する可燃性ガス吹出口9の位置と、ガ
ス燃焼室8への空気供給管16の位置の関係は、
可燃性ガスが一次反応室1よりガス燃焼室8へ吸
引される如きエジエクテイング効果が得られるよ
う構成されることが望ましい。
The relationship between the position of the combustible gas outlet 9 that supplies flammable gas from the primary reaction chamber 1 to the gas combustion chamber 8 and the position of the air supply pipe 16 to the gas combustion chamber 8 is as follows.
It is desirable that the structure is such that an ejecting effect such as combustible gas is sucked from the primary reaction chamber 1 into the gas combustion chamber 8 can be obtained.

また、ガス燃焼室8にて生成される帯熱廃ガス
を排ガス口15に導出する代りに、熱ガス供給口
17を介して、ボイラー・乾燥機・加熱機等の熱
利用装置に導入する如く構成すれば、効果的であ
る。
Alternatively, instead of leading the heated waste gas generated in the gas combustion chamber 8 to the exhaust gas port 15, it may be introduced into a heat utilization device such as a boiler, dryer, or heater through the hot gas supply port 17. It is effective if configured.

[発明の効果] 本発明では、一次反応室への空気の制御送入及
び水蒸気の制御送入により、被処理物中の有機物
質に不完全燃焼及び熱分解を生じさせると共にそ
の有機物質から生成した炭分と水蒸気との間で水
性ガスを発生させることによつて、被処理物中に
おける回収すべき金属の品質劣化を防止し得る程
度に高温化を抑制し、而も一酸化炭素ガス及び水
素ガスによる還元作用により金属の酸化を防い
で、回収される有価金属の品質向上及び回収率ア
ツプを実現し得る。すなわち例えば廃却電線の回
収率において、従来装置の80%に対して95%以上
を実現し得る。而も、炭分の消化により金属の回
収を容易にすると共に炭分処理作業を省力化する
ことができる。
[Effects of the Invention] In the present invention, by controlling the supply of air and the controlled supply of water vapor to the primary reaction chamber, incomplete combustion and thermal decomposition are caused in the organic substances in the material to be treated, and the organic substances are generated from the organic substances. By generating water gas between the carbon monoxide and water vapor, the temperature increase can be suppressed to an extent that can prevent quality deterioration of the metal to be recovered in the treated material, and carbon monoxide gas and The reducing action of hydrogen gas prevents oxidation of metals, making it possible to improve the quality of recovered valuable metals and increase the recovery rate. That is, for example, in terms of the recovery rate of discarded electric wires, it is possible to achieve a recovery rate of 95% or more, compared to 80% with conventional devices. Moreover, by digesting the charcoal, metals can be easily recovered and the labor required to process the charcoal can be saved.

また、不完全燃焼、熱分解及び水性ガス反応に
よる可燃性のガスの効率的生成等によつて実現さ
れるガス燃焼室での理想的な完全燃焼状態によ
り、排ガス熱を効率的に利用し得ると共に、排ガ
ス中のダスト濃度が極めて低くなつて集塵装置等
の付帯をほとんど要しない。
In addition, exhaust gas heat can be used efficiently due to the ideal complete combustion state in the gas combustion chamber, which is achieved through incomplete combustion, thermal decomposition, and efficient generation of flammable gas through water gas reactions. At the same time, the dust concentration in the exhaust gas is extremely low, so there is almost no need for accessories such as dust collectors.

更に、サーマルNOxの生成をも低減させるこ
とができ、必要によりガス燃焼室へ空気と共に水
蒸気を供給することによつてガス燃焼室内のサー
マルNOxを従来装置の半分に減少させ得る。
Furthermore, the generation of thermal NO x can also be reduced, and by supplying steam together with air to the gas combustion chamber, if necessary, the thermal NO x in the gas combustion chamber can be reduced to half that of conventional devices.

【図面の簡単な説明】[Brief explanation of the drawing]

図面は何れも本発明の1実施例についてのもの
であつて、第1図は装置の縦断面図、第2図はそ
の横断平面図、第3図は、第1図におけるAA線
縦断面図である。 図面中、1は一次反応室、2は供空機、3……
3は制御弁、4は空気供給管、5は一次反応室底
床部、6……6は空気吹出口、7は水蒸気供給
管、8はガス燃焼室、9は可燃性ガス吹出口、1
0は供空機、11は水蒸気供給管、12は助燃バ
ーナ、13は天蓋、14は回収扉、15は排ガス
口、16は空気供給管、17は熱ガス供給口であ
る。
The drawings are all about one embodiment of the present invention, and FIG. 1 is a longitudinal sectional view of the device, FIG. 2 is a cross-sectional plan view thereof, and FIG. 3 is a longitudinal sectional view taken along the line AA in FIG. 1. It is. In the drawing, 1 is the primary reaction chamber, 2 is the supply aircraft, 3...
3 is a control valve, 4 is an air supply pipe, 5 is a bottom floor of the primary reaction chamber, 6...6 is an air outlet, 7 is a steam supply pipe, 8 is a gas combustion chamber, 9 is a combustible gas outlet, 1
0 is an air supply machine, 11 is a steam supply pipe, 12 is an auxiliary combustion burner, 13 is a canopy, 14 is a recovery door, 15 is an exhaust gas port, 16 is an air supply pipe, and 17 is a hot gas supply port.

Claims (1)

【特許請求の範囲】 1 少なくとも固形可燃性有機物質と金属とを混
合状態で含む被処理物から金属を回収する方法で
あつて、 一次反応室に前記被処理物を収容させて着火し
た後、 その被処理物中の有機物質に不完全燃焼及び熱
分解が生ずるように一次反応室に空気を制御送入
することによつて可燃性ガスを発生させ、 不完全燃焼及び熱分解により被処理物中の有機
物質から生成した炭分との間で水性ガス反応が生
ずるように一次反応室に水蒸気を制御送入するこ
とによつて、水性ガスを発生させると共に被処理
物中における回収すべき金属の品質劣化を防止し
得る程度に高温化を抑制し、 一次反応室において有機物質の不完全燃焼及び
熱分解により発生した可燃性ガス及び水性ガス反
応により発生した水性ガスをガス燃焼室に導くと
共にそのガス燃焼室に空気又は空気及び水蒸気を
送入し、 一般燃料による助燃バーナによつて一時的に助
燃することにより前記可燃性ガス及び水性ガスの
継続的自燃を行わせることを特徴とするガス化燃
焼による金属回収方法。 2 少なくとも固形可燃性有機物質と金属とを混
合状態で含む被処理物から金属を回収するための
装置であつて、 前記被処理物を容入する一次反応室と、 被処理物中の有機物質に不完全燃焼及び熱分解
が生じて可燃性ガスが発生するように一次反応室
に空気を制御送入するための空気制御送入手段
と、 不完全燃焼及び熱分解により被処理物中の有機
物質から生成した炭分との間で水性ガス反応が生
じて水性ガスを発生させると共に被処理物中にお
ける回収すべき金属の品質劣化を防止し得る程度
に高温化が抑制されるように一次反応室に水蒸気
を制御送入するための水蒸気制御送入手段と、 一次反応室において有機物質の不完全燃焼及び
熱分解により発生した可燃性ガス及び水性ガス反
応により発生した水性ガスが導かれるガス燃焼室
と、 ガス燃焼室に空気又は空気及び水蒸気を送入す
るための送入手段と、 一時的に助燃することにより前記可燃性ガス及
び水性ガスの継続的自燃を行わせるための一般燃
料による助燃バーナとを備えることを特徴とする
金属回収用ガス化燃焼装置。 3 ガス燃焼室が、ボイラー・乾燥器・加熱炉等
の熱利用装置に連通する熱ガス供給口を有する特
許請求の範囲第2項記載の金属回収用ガス化燃焼
装置。 4 一次反応室が、被処理物中の可燃性物質のガ
ス化燃焼後、残存金属を回収するための開閉自在
の回収扉を具備する特許請求の範囲第2項記載の
金属回収用ガス化燃焼装置。
[Scope of Claims] 1. A method for recovering metal from a workpiece containing at least a solid combustible organic substance and a metal in a mixed state, the method comprising: storing the workpiece in a primary reaction chamber and igniting the workpiece; Combustible gas is generated by controlling air flow into the primary reaction chamber to cause incomplete combustion and thermal decomposition of the organic substances in the material to be treated, and the material to be treated is destroyed by incomplete combustion and thermal decomposition. By controllingly feeding water vapor into the primary reaction chamber so as to cause a water gas reaction with the carbon produced from the organic materials in the material, water gas is generated and the metal to be recovered in the material to be treated is removed. flammable gas generated by incomplete combustion and thermal decomposition of organic substances in the primary reaction chamber and water gas generated by water gas reaction are guided to the gas combustion chamber. A gas characterized in that air or air and water vapor are introduced into the gas combustion chamber, and the combustible gas and water gas are caused to continuously self-combust by temporarily auxiliary combustion using an auxiliary combustion burner using a general fuel. Metal recovery method by chemical combustion. 2. An apparatus for recovering metals from a workpiece containing at least a solid combustible organic substance and a metal in a mixed state, comprising: a primary reaction chamber containing the workpiece; and an organic substance in the workpiece. air control feeding means for controllingly feeding air into the primary reaction chamber so that incomplete combustion and thermal decomposition occur to generate flammable gas; and A water gas reaction occurs with the carbon produced from the substance to generate water gas, and the primary reaction is performed so that the temperature rise is suppressed to an extent that can prevent quality deterioration of the metal to be recovered in the material to be treated. a steam control feed means for controlling steam to be fed into the chamber; and a gas combustion system in which flammable gases generated by incomplete combustion and thermal decomposition of organic substances and water gases generated by water gas reactions are introduced into the primary reaction chamber. a feeding means for feeding air or air and water vapor into the gas combustion chamber; and auxiliary combustion with general fuel to cause continuous self-combustion of the flammable gas and water gas by temporarily auxiliary combustion. A gasification combustion device for metal recovery, characterized by comprising a burner. 3. The gasification and combustion apparatus for metal recovery according to claim 2, wherein the gas combustion chamber has a hot gas supply port communicating with a heat utilization device such as a boiler, dryer, or heating furnace. 4. Gasification and combustion for metal recovery according to claim 2, wherein the primary reaction chamber is equipped with a recovery door that can be opened and closed to recover residual metal after gasification and combustion of flammable substances in the object to be treated. Device.
JP60183702A 1985-08-20 1985-08-20 Gasifying burner for solid combustion matter Granted JPS6246117A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP60183702A JPS6246117A (en) 1985-08-20 1985-08-20 Gasifying burner for solid combustion matter

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP60183702A JPS6246117A (en) 1985-08-20 1985-08-20 Gasifying burner for solid combustion matter

Publications (2)

Publication Number Publication Date
JPS6246117A JPS6246117A (en) 1987-02-28
JPH0523328B2 true JPH0523328B2 (en) 1993-04-02

Family

ID=16140452

Family Applications (1)

Application Number Title Priority Date Filing Date
JP60183702A Granted JPS6246117A (en) 1985-08-20 1985-08-20 Gasifying burner for solid combustion matter

Country Status (1)

Country Link
JP (1) JPS6246117A (en)

Families Citing this family (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH0545422U (en) * 1991-11-12 1993-06-18 ユニ・コンサルタンツ株式会社 Gasification combustion type incinerator of waste
JPH05280720A (en) * 1992-03-31 1993-10-26 Koji Kuboyama Scrapped vessel incinerating furnace
JP5762713B2 (en) * 2010-10-04 2015-08-12 株式会社キンセイ産業 Dry distillation gasification incineration processing equipment
DE102011122139A1 (en) * 2011-12-22 2013-06-27 Heraeus Precious Metals Gmbh & Co. Kg Process for burning off carbonaceous dry metallic ash

Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS5755840B2 (en) * 1978-12-25 1982-11-26
JPS57202409A (en) * 1981-03-27 1982-12-11 Enu Beeshitsuku Shinia Jiyon Garbage furnace system and its incinerating method
JPS597888A (en) * 1982-07-02 1984-01-17 Kubota Ltd Container for heat-accumulating material and production thereof

Family Cites Families (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS5755840U (en) * 1980-09-12 1982-04-01

Patent Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS5755840B2 (en) * 1978-12-25 1982-11-26
JPS57202409A (en) * 1981-03-27 1982-12-11 Enu Beeshitsuku Shinia Jiyon Garbage furnace system and its incinerating method
JPS597888A (en) * 1982-07-02 1984-01-17 Kubota Ltd Container for heat-accumulating material and production thereof

Also Published As

Publication number Publication date
JPS6246117A (en) 1987-02-28

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