JP2004090004A - Industrial waste treatment plant - Google Patents

Industrial waste treatment plant Download PDF

Info

Publication number
JP2004090004A
JP2004090004A JP2003354311A JP2003354311A JP2004090004A JP 2004090004 A JP2004090004 A JP 2004090004A JP 2003354311 A JP2003354311 A JP 2003354311A JP 2003354311 A JP2003354311 A JP 2003354311A JP 2004090004 A JP2004090004 A JP 2004090004A
Authority
JP
Japan
Prior art keywords
slag
melting furnace
industrial waste
melting
molten
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.)
Granted
Application number
JP2003354311A
Other languages
Japanese (ja)
Other versions
JP4216160B2 (en
Inventor
Hiromi Mochida
持田 裕美
Akiyoshi Tatsui
辰亥 昭善
Fumihiko Ogino
荻野 文彦
Noboru Iwata
岩田 昇
Koretaka Ishikawa
石河 是孝
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.)
Mitsubishi Materials Corp
Sumitomo Heavy Industries Ltd
Original Assignee
Mitsubishi Materials Corp
Sumitomo Heavy Industries 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 Mitsubishi Materials Corp, Sumitomo Heavy Industries Ltd filed Critical Mitsubishi Materials Corp
Priority to JP2003354311A priority Critical patent/JP4216160B2/en
Publication of JP2004090004A publication Critical patent/JP2004090004A/en
Application granted granted Critical
Publication of JP4216160B2 publication Critical patent/JP4216160B2/en
Anticipated expiration legal-status Critical
Expired - Lifetime legal-status Critical Current

Links

Images

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

Landscapes

  • Processing Of Solid Wastes (AREA)
  • Manufacture And Refinement Of Metals (AREA)
  • Treatment Of Steel In Its Molten State (AREA)
  • Furnace Charging Or Discharging (AREA)
  • Muffle Furnaces And Rotary Kilns (AREA)
  • Furnace Details (AREA)
  • Incineration Of Waste (AREA)
  • Gasification And Melting Of Waste (AREA)

Abstract

<P>PROBLEM TO BE SOLVED: To provide an industrial waste treatment plant in which industrial wastes W1, W2 containing metals is introduced into and melted in a rotary kiln type melting furnace 2 and molten metals M can be recovered separately from slag S. <P>SOLUTION: The plant comprises the rotary kiln type melting furnace 2 in which the industrial wastes W1, W2 is melted, water granulation means 4 for water granulating a fluid F produced in the melting furnace 2 comprising molten metals M and molten slag S, and a charging mechanism 1 for introducing the industrial wastes W1, W2 and flux into the melting furnace 2, wherein the molten metals M are separated from the molten slag S in the melting furnace 2 due to the specific gravity difference between them by introducing the flux into the melting furnace 2 so as to increase the fluidity of the molten slag S. The water granulation means 4 comprises a water tank 41 in which the fluid F discharged from the melting furnace 2 is water granulated. The molten metals M and the molten slag S separated from each other flow down out of the melting furnace 2 into the water tank 41 and water granulated therein. Thus, metal cakes and slag cakes are recovered separately from each other. <P>COPYRIGHT: (C)2004,JPO

Description

 本発明は、産業廃棄物処理装置に関するものであり、特に金属含有産業廃棄物を高温溶融炉内で溶融する際に、この溶融によって溶出する溶融金属をスラグから分離して回収し得るようにした産業廃棄物処理装置に関する。 The present invention relates to an industrial waste treatment apparatus, and particularly when metal-containing industrial waste is melted in a high-temperature melting furnace, molten metal eluted by this melting can be separated and recovered from slag. The present invention relates to an industrial waste treatment device.

 自動車や家庭電化製品などの金属含有産業廃棄物を処理する一方法として、これらの産業廃棄物を高温の溶融炉で溶融する方法が用いられている。この溶融による処理方法の一例を図2により説明する。図2において前記産業廃棄物W1 またはその解砕物W2はロータリーキルン60の基部に設けられた導入口62から導入され、この基部に設置された第1バーナー63によって熱風が供給され、例えば1400℃以上の温度で溶融される。この溶融によって産業廃棄物中の可燃物は熱分解されてガス化し、一方、金属を含む不燃性物質はロータリーキルン内の前記温度によって溶融状態または半溶融状態の流動体Fになる。 (4) As one method of treating metal-containing industrial waste such as automobiles and home appliances, a method of melting these industrial wastes in a high-temperature melting furnace is used. An example of a processing method using this melting will be described with reference to FIG. In FIG. 2, the industrial waste W1 or the crushed product W2 is introduced from an inlet 62 provided at a base of a rotary kiln 60, and hot air is supplied by a first burner 63 provided at the base. Melted at temperature. This melting causes the combustibles in the industrial waste to be thermally decomposed and gasified, while the non-combustible substances containing metals become a molten or semi-molten fluid F depending on the temperature in the rotary kiln.

 生成したガス成分はロータリーキルンの開放端部65から2次燃焼室3に送られ、この2次燃焼室3で更に第2バーナー34からの熱風と空気供給管35からの空気の供給を受けて高温で燃焼されて例えばダイオキシンや悪臭物質などが分解され、2次燃焼室の排出口33から燃焼ガスGとして排出される。この燃焼ガスGは、図示しないが更に熱交換工程、ダイオキシン再生成防止のためのクエンチ工程、煤塵・有害ガス除去工程などを経て大気中に放出される。 The generated gas component is sent from the open end 65 of the rotary kiln to the secondary combustion chamber 3, where the hot air from the second burner 34 and the air supply from the air supply pipe 35 are further supplied to the secondary combustion chamber 3. And decomposes, for example, dioxin and malodorous substances, and is discharged as combustion gas G from an outlet 33 of the secondary combustion chamber. Although not shown, the combustion gas G is further released into the atmosphere through a heat exchange step, a quench step for preventing dioxin regeneration, a dust and harmful gas removal step, and the like.

 ロータリーキルン内に生成した流動体Fは、このロータリーキルンの胴部61の傾斜に沿って流動し、開放端部65から水砕ピット4に排出される。水砕ピット4に導入された流動体Fは、この水砕ピット4内で水冷されると共に破砕され、結晶性または非結晶性の砕塊Rとなり、コンベア42によって搬出される。この砕塊Rは従来から埋立てや建設資材などの土木建設用として用いられている。 The fluid F generated in the rotary kiln flows along the inclination of the body 61 of the rotary kiln, and is discharged from the open end 65 to the granulation pit 4. The fluid F introduced into the granulation pit 4 is water-cooled and crushed in the granulation pit 4 to form a crystalline or non-crystalline crushed mass R, which is carried out by the conveyor 42. This crushed mass R has been conventionally used for civil engineering construction such as landfill and construction materials.

 前記産業廃棄物の処理方法において、溶融によってロータリーキルン内に生成する流動体Fは、一般に金属とスラグとの混成物である。このスラグの組成は通常、SiO/Al/CaOを主成分とするものであって、一例を挙げれば、SiOが32〜45重量%、Alが10〜30重量%、CaOが7〜14重量%を占め、残部がFe酸化物などとなっている。この組成を有するスラグは溶融温度が高くしかも溶融物の粘度が高いので、例えば前記のロータリーキルン60内を水砕ピット4に向けて流動させるためには炉内温度を1400℃以上とする必要があった。またこの高温に耐えるため、ロータリーキルンの内張り耐火物としてはアルミナ系耐火煉瓦が用いられていた。 In the method for treating industrial waste, the fluid F generated in the rotary kiln by melting is generally a composite of metal and slag. The composition of the slag is typically a mainly composed of SiO 2 / Al 2 O 3 / CaO, in one example, SiO 2 is 32 to 45 wt%, Al 2 O 3 is 10 to 30 wt% , CaO accounts for 7 to 14% by weight, and the remainder is Fe oxide or the like. Since the slag having this composition has a high melting temperature and a high viscosity of the melt, for example, in order to flow the inside of the rotary kiln 60 toward the granulation pit 4, the furnace temperature needs to be 1400 ° C or more. Was. To withstand this high temperature, alumina-based refractory bricks have been used as a refractory lining of a rotary kiln.

 前記の産業廃棄物処理方法において、得られた砕塊RにはFeを始めとしてCu、Au、Agなどの有用な、または高価な金属が含まれている。しかし、これまでそれら有用金属の回収は試みられていなかった。その理由は、ロータリーキルン内における前記流動体Fの粘度が、前記スラグの高溶融温度・高粘度に起因して極めて高いので、ロータリーキルン内で溶融金属と溶融スラグとが混成体を形成して分離せず、この流動体Fを水砕ピット4で解砕した後に得られる砕塊Rを選別して金属を回収する作業が経済的に引き合わなかったからである。高温のため、スラグ中で酸化も促進され、特にCuが酸化され、溶融金属層が形成され難かったこともある。
 また前記の産業廃棄物処理方法では、前記のようにロータリーキルン内における流動体Fの溶融温度が高いことに起因して、ロータリーキルンの内壁が熔損しやすく、溶融炉の耐用期間が短いという問題もあった。
 本発明は前記の課題を解決するためになされたものであって、従ってその第一の目的は、金属含有産業廃棄物を溶融炉内に導入して溶融するに際して、この溶融によって溶出する溶融金属をスラグから分離して回収し得るようにした産業廃棄物処理方法を提供することにある。また本発明の第二の目的は、溶融炉の熔損を防止して溶融炉の耐用期間を延長することにある。
In the above-mentioned method for treating industrial waste, the obtained crushed mass R contains useful metals or expensive metals such as Fe, Cu, Au and Ag. However, recovery of such useful metals has not been attempted so far. The reason is that the viscosity of the fluid F in the rotary kiln is extremely high due to the high melting temperature and high viscosity of the slag, so that the molten metal and the molten slag form a hybrid and separate in the rotary kiln. This is because the operation of selecting the crushed mass R obtained after crushing the fluid F in the water crushing pit 4 and collecting the metal was not economically satisfactory. Owing to the high temperature, oxidation is promoted in the slag, and particularly, Cu is oxidized, and it has been difficult to form a molten metal layer.
Further, in the above-mentioned industrial waste treatment method, there is also a problem that the inner wall of the rotary kiln is easily melted due to the high melting temperature of the fluid F in the rotary kiln as described above, and the service life of the melting furnace is short. Was.
SUMMARY OF THE INVENTION The present invention has been made to solve the above-mentioned problems, and a first object of the present invention is to introduce a molten metal which is eluted by melting when metal-containing industrial waste is introduced into a melting furnace and melted. It is an object of the present invention to provide an industrial waste treatment method capable of separating and recovering slag from slag. A second object of the present invention is to prevent the melting of the melting furnace and extend the service life of the melting furnace.

 前記の課題を解決するために本発明は、金属含有産業廃棄物を溶融するロータリーキルン式溶融炉と、該溶融炉内で生成された溶融金属および溶融スラグからなる流動体を冷却、破砕する冷却破砕手段とを備える産業廃棄物処理装置であって、前記産業廃棄物およびスラグ溶融剤を前記溶融炉内に導入する搬入機構を備え、前記スラグ溶融剤を前記溶融炉内へ導入することによって、該溶融炉内における前記産業廃棄物の溶融により生成するスラグの溶融温度が1400℃以下となるようにこのスラグの塩基度(CaO/SiO重量比)を調整し、前記溶融スラグの流動性を増大させることにより、前記溶融炉内で前記溶融金属と前記溶融スラグとをこれらの比重差により分離する構成とされ、前記冷却破砕手段は、前記溶融炉から排出される前記流動体を冷却し破砕する水槽を備え、前記溶融金属と前記溶融スラグとを互いが分離した状態で前記溶融炉から流下させ、前記水槽内で冷却破砕し、金属とスラグとを別の砕塊として得る構成とされたことを特徴とする。 In order to solve the above-described problems, the present invention provides a rotary kiln type melting furnace for melting metal-containing industrial waste, and cooling and crushing for cooling and crushing a fluid comprising molten metal and molten slag generated in the melting furnace. And an industrial waste treatment apparatus comprising means for introducing the industrial waste and the slag melt into the melting furnace, and introducing the slag melt into the melting furnace. The basicity of the slag (CaO / SiO 2 weight ratio) is adjusted so that the melting temperature of the slag generated by melting the industrial waste in the melting furnace is 1400 ° C. or less, and the fluidity of the molten slag is increased. In the melting furnace, the molten metal and the molten slag are separated from each other by a difference in their specific gravities, and the cooling and crushing means discharges the molten slag from the melting furnace. A water tank for cooling and crushing the fluid to be flowed down from the melting furnace in a state where the molten metal and the molten slag are separated from each other, and cooled and crushed in the water tank to separate the metal and the slag. It is characterized by being obtained as a crushed mass.

 一般に前記産業廃棄物をロータリーキルン式溶融炉内に導入して溶融すると、産業廃棄物に含まれていた金属が溶出すると共にスラグが生成する。このスラグは、その塩基度を特定範囲内に調整すると、結晶組成の変化が起こって溶融温度が1400℃以下に低下する。そして溶融温度が1400℃以下となる結晶組成の領域では、溶融スラグの粘度が著しく低下することがわかった。従って、スラグの溶融温度が1400℃以下となるようにその塩基度を調整すれば、溶融スラグの粘度が低下して流動性が増し、温度低下とともに溶融金属がスラグの下層となって酸素と接触しなくなるため、その酸化が防止され、ロータリーキルン式溶融炉内で溶融スラグと溶融金属とがその比重差によって良好に分離するようになる。
 ロータリーキルン式溶融炉内で溶融金属と溶融スラグとが良好に分離していれば、この溶融炉から冷却破砕手段としての水砕ピットなどに導入して冷却解砕した際に、金属とスラグとが互いに異なる砕塊として得られるので、例えば磁気選鉱法などによって金属砕塊を選別し、高い回収率で金属を回収することができる。
 また、ロータリーキルン式溶融炉であれば、傾斜した回転筒状溶融炉の上方端部から産業廃棄物を導入し加熱溶融することにより、溶融金属と溶融スラグとが良好に分離した状態で下方の開放端部から連続的に排出されるので、容易かつ連続的に金属を回収することができる。
Generally, when the industrial waste is introduced into a rotary kiln-type melting furnace and melted, metal contained in the industrial waste is eluted and slag is generated. When the basicity of the slag is adjusted to a specific range, a change in crystal composition occurs, and the melting temperature decreases to 1400 ° C. or lower. It was found that the viscosity of the molten slag was significantly reduced in the region of the crystal composition where the melting temperature was 1400 ° C. or lower. Therefore, if the basicity is adjusted so that the melting temperature of the slag becomes 1400 ° C. or less, the viscosity of the molten slag decreases and the fluidity increases, and as the temperature decreases, the molten metal becomes a lower layer of the slag and comes into contact with oxygen. Therefore, the oxidation is prevented, and the molten slag and the molten metal are separated well in the rotary kiln type melting furnace due to the difference in specific gravity.
If the molten metal and the molten slag are well separated in the rotary kiln type melting furnace, the metal and the slag are separated from each other when they are introduced from this melting furnace into a granulation pit as cooling crushing means and cooled and crushed. Since they are obtained as different crushed masses, crushed metal lumps can be sorted out by, for example, a magnetic separation method, and the metal can be collected at a high recovery rate.
In the case of a rotary kiln type melting furnace, industrial waste is introduced from the upper end of the inclined rotary cylindrical melting furnace and is heated and melted, so that the molten metal and the molten slag are opened downward in a well separated state. Since the metal is continuously discharged from the end, the metal can be collected easily and continuously.

 前記において、前記冷却破砕手段により得られた砕塊を金属の破塊とスラグの破塊とに分別する磁気選鉱装置を備えることを特徴とする。
 この場合、金属の砕塊として、特に、銅および金などの貴金属を始めとする各種金属を高い回収率で確実に回収することができる。
 また、前記において、スラグの塩基度は、0.35〜1.35の範囲内に調整することが好ましい。
 各種産業廃棄物から生成するスラグの元来の溶融温度は、前記のように概略1400℃以上であるが、個別にはその産業廃棄物の組成により異なっている。しかし、いずれの産業廃棄物においても、スラグの塩基度を前記範囲内に調整すれば、その溶融温度を1400℃以下に降下させることができる。塩基度が0.35未満では、スラグの溶融温度を1400℃以下にすることが困難である。塩基度が1.35を越えると、この調整のために要するスラグ溶融剤の量が多くなって排出されるスラグ量が多くなり運転効率が低下する。
In the above, there is provided a magnetic ore separation apparatus for separating the crushed mass obtained by the cooling crushing means into metal crushed fragments and slag crushed fragments.
In this case, various kinds of metals including noble metals such as copper and gold can be surely recovered at a high recovery rate as crushed metals.
In the above, it is preferable that the basicity of the slag is adjusted within the range of 0.35 to 1.35.
The original melting temperature of slag generated from various industrial wastes is approximately 1400 ° C. or higher as described above, but individually varies depending on the composition of the industrial waste. However, in any of the industrial wastes, if the basicity of the slag is adjusted within the above range, the melting temperature can be lowered to 1400 ° C. or less. If the basicity is less than 0.35, it is difficult to reduce the slag melting temperature to 1400 ° C. or lower. If the basicity exceeds 1.35, the amount of slag flux required for this adjustment increases, the amount of slag discharged increases, and the operating efficiency decreases.

 前記スラグの塩基度は、CaOを含むスラグ溶融剤の添加により調整することが好ましい。
 一般に、自動車や家庭電化製品などの金属含有産業廃棄物を溶融したときに生成するスラグの塩基度(CaO/SiO重量比)は、0.15〜0.3程度である。これを、スラグの溶融温度を1400℃以下とする塩基度(0.35〜1.35)と比較するとCaOが不足している。従って、CaOを含むスラグ溶融剤を溶融炉に添加することにより塩基度を前記0.35〜1.35の範囲内に調整することができる。CaOを含むスラグ溶融剤の例としては、例えば石灰石、消石灰、CaOを含む中和沈澱物、または他の製造工程で得られるCaOに富むスラグなどを挙げることができる。
The basicity of the slag is preferably adjusted by adding a slag flux containing CaO.
Generally, the basicity of slag produced upon melting the metal-containing industrial wastes, such as automobiles and household appliances (CaO / SiO 2 weight ratio) is about 0.15 to 0.3. When this is compared with the basicity (0.35 to 1.35) at which the melting temperature of the slag is 1400 ° C or lower, CaO is insufficient. Therefore, the basicity can be adjusted to the range of 0.35 to 1.35 by adding the slag flux containing CaO to the melting furnace. Examples of CaO-containing slag melting agents include, for example, limestone, slaked lime, neutralized precipitates containing CaO, or slags rich in CaO obtained in other production processes.

 前記溶融炉内には、C(炭素)を含む還元剤を添加してもよい。
 前記産業廃棄物を溶融炉内で溶融するに際して、少なくとも溶融物は、金属の酸化によるスラグへの移行を防ぐために還元雰囲気下に置くことが好ましい。産業廃棄物中に有機物質などのC成分(可燃物)が多く含まれている場合はこれら未燃焼のC成分が溶融炉内の溶融物に溶け込み還元雰囲気を形成するので問題ないが、既に焼却処理されたものとか、少ない場合は、産業廃棄物の処理量に対して2重量%〜20重量%程度のCを含む還元剤を添加すれば、有価金属を還元でき、溶融金属が酸化によってスラグ側に移行することによる金属の損失を防止することができる。Cを含む還元剤の例としては、好ましくはコークス、他に粉炭、石炭、有機物廃材などを挙げることができる。
A reducing agent containing C (carbon) may be added into the melting furnace.
When the industrial waste is melted in a melting furnace, at least the melt is preferably placed in a reducing atmosphere in order to prevent a shift to slag due to oxidation of the metal. If the industrial waste contains a large amount of C components (combustibles) such as organic substances, there is no problem because these unburned C components are dissolved into the melt in the melting furnace to form a reducing atmosphere, but there is no problem. If the amount is reduced, or if the amount is small, a valuable metal can be reduced by adding a reducing agent containing C in an amount of about 2% to 20% by weight based on the amount of the industrial waste to be processed, and the molten metal is converted into slag by oxidation. The metal loss due to the shift to the side can be prevented. Examples of the reducing agent containing C preferably include coke, pulverized coal, coal, and organic waste materials.

 前記溶融炉内の少なくとも前記スラグが接触する部分は、MgOを主成分とする塩基性マグネシア系耐火材で被覆することが好ましい。
 前記のようにスラグの溶融温度を1400℃以下とするためにCaOを含むスラグ溶融剤を添加して塩基度を高くすると、従来から溶融炉の内壁に用いられているアルミナ系耐火材は、その耐火材中のAl成分と前記スラグ溶融剤中のCaOとが反応して低融点化合物を形成し、炉の耐久性を低下させる。炉壁の耐火材として前記のMgOを主成分とする塩基性マグネシア系耐火材を用いれば、塩基度を高くしても炉壁が侵食されることはなく、溶融炉の耐久性が向上する。
It is preferable that at least a portion of the melting furnace in contact with the slag is coated with a basic magnesia-based refractory material containing MgO as a main component.
When the slag melting agent containing CaO is added to increase the basicity in order to reduce the melting temperature of the slag to 1400 ° C. or less as described above, the alumina-based refractory material conventionally used for the inner wall of the melting furnace is The Al 2 O 3 component in the refractory material and the CaO in the slag melting agent react to form a low-melting compound, thereby lowering the durability of the furnace. If the basic magnesia-based refractory material containing MgO as a main component is used as the refractory material for the furnace wall, the furnace wall is not eroded even if the basicity is increased, and the durability of the melting furnace is improved.

 本発明の産業廃棄物処理装置は、処理物の形状を問わずに処理可能であるとともに、溶融によって生成するスラグの溶融温度が1400℃以下となるようにこのスラグの塩基度を調整するものであるので、金属含有産業廃棄物を溶融炉内に導入して溶融するに際して、金属とスラグとを容易に分離することができ、有用金属または高価金属が有利に回収できるようになる。 The industrial waste treatment apparatus of the present invention can treat regardless of the shape of the treated material, and adjusts the basicity of the slag so that the melting temperature of the slag generated by melting is 1400 ° C. or less. Therefore, when the metal-containing industrial waste is introduced into the melting furnace and melted, the metal and the slag can be easily separated, and the useful metal or the expensive metal can be advantageously recovered.

 以下、本発明の実施の形態を図面を用いて説明する。
 図1は本発明の産業廃棄物処理装置の一例を示している。この処理装置は、基本的には図2に示した従来の処理装置と同様であるが、ただしロータリーキルンの内壁が塩基性マグネシア系煉瓦、具体的にはマグネシア・クロミア煉瓦で覆われている。
Hereinafter, embodiments of the present invention will be described with reference to the drawings.
FIG. 1 shows an example of the industrial waste treatment apparatus of the present invention. This processing apparatus is basically the same as the conventional processing apparatus shown in FIG. 2, except that the inner wall of the rotary kiln is covered with a basic magnesia brick, specifically, a magnesia-chromia brick.

 図1において、この産業廃棄物処理装置は概略、搬入機構1と、ロータリーキルン式溶融炉2と、2次燃焼室3と、水砕ピット(冷却破砕手段)4とからなっている。
 搬入機構1は、処理する産業廃棄物の状態に応じて、大型の産業廃棄物W1を搬入する機構11と、解砕されたまたは小型の産業廃棄物W2をコンベアで搬入する機構12とを備えている。
 ロータリーキルン式溶融炉2は、円筒状の胴部21が基部から開放端部25に向けて下方に傾斜するように設置され、回転機構24,24によって円筒の中心軸を回転軸として回転するようになっている。この胴部21の内壁は、前記のようにマグネシア・クロミア煉瓦で覆われている。また胴部21の中間部には、図示しないが中間加熱設備が設けられている。
 ロータリーキルン式溶融炉2の基部には産業廃棄物W1,W2の導入口22と、第1バーナー23とが設けられ、下方の開放端部25は2次燃焼室3の下端部に開放されている。
In FIG. 1, the industrial waste treatment apparatus generally includes a carry-in mechanism 1, a rotary kiln-type melting furnace 2, a secondary combustion chamber 3, and a granulation pit (cooling and crushing means) 4.
The carrying-in mechanism 1 includes a mechanism 11 for carrying in a large-sized industrial waste W1 and a mechanism 12 for carrying in a crushed or small-sized industrial waste W2 according to the state of the industrial waste to be treated. ing.
The rotary kiln type melting furnace 2 is installed such that the cylindrical body 21 is inclined downward from the base toward the open end 25, and is rotated by the rotation mechanisms 24, 24 about the center axis of the cylinder as the rotation axis. Has become. The inner wall of the body 21 is covered with magnesia-chromia brick as described above. An intermediate heating facility (not shown) is provided at an intermediate portion of the body 21.
At the base of the rotary kiln type melting furnace 2, an inlet 22 for industrial waste W 1, W 2 and a first burner 23 are provided, and a lower open end 25 is open to a lower end of the secondary combustion chamber 3. .

 2次燃焼室3は立設された管体であって、下端部には水砕ピット4に通じる流動体の排出口31が設けられ、その上方の管壁に、前記ロータリーキルンの開放端部25を受ける開口32が形成されている。また、2次燃焼室3の上部には排出口33が設けられて、図示しない排ガス後処理装置とダクトで連結されている。この2次燃焼室3の中間部には、排ガスを高温で燃焼するための第2バーナー34と空気供給管35とが設けられている。前記排ガス後処理装置は、熱交換器、ダイオキシン再生成防止のためのクエンチ装置、煤塵・有害ガス除外装置などを含み、これらの装置を経由した排ガスは最終的に大気中に放出される。
 水砕ピット4は、ロータリーキルンの開放端部25から排出された流動体を冷却し破砕する水槽41と、破砕された砕塊Rを搬出するコンベア42とを有している。
The secondary combustion chamber 3 is an upright pipe, and a discharge port 31 for the fluid leading to the granulation pit 4 is provided at the lower end, and the open end 25 of the rotary kiln is provided on the pipe wall above the pipe. Receiving opening 32 is formed. A discharge port 33 is provided at an upper portion of the secondary combustion chamber 3 and is connected to an exhaust gas after-treatment device (not shown) by a duct. An intermediate portion of the secondary combustion chamber 3 is provided with a second burner 34 for burning exhaust gas at a high temperature and an air supply pipe 35. The exhaust gas aftertreatment device includes a heat exchanger, a quench device for preventing dioxin regeneration, a device for removing dust and harmful gases, and the like, and the exhaust gas passing through these devices is finally released into the atmosphere.
The water crushing pit 4 has a water tank 41 for cooling and crushing the fluid discharged from the open end 25 of the rotary kiln, and a conveyor 42 for discharging the crushed lumps R.

 次に前記産業廃棄物処理装置を用いる本発明の一実施形態について説明する。
 先ずロータリーキルン2の胴部21を回転し、第1バーナー23を点火して胴部21内部を1400℃以下の適温、例えば1350℃に加熱しておく。
 次に、例えば廃自動車のプレス解砕体(産業廃棄物W2)をコンベア付きの搬入機構12によってロータリーキルンの基部に搬送し、導入口22から胴部21内に導入する。なお、プレス解砕体は、ロータリーキルン方式では、形状は特に問題とせず、粉体状でも一体物でも投入できるものであれば、溶融処理可能である。他の溶融炉方式(例えばガス化溶融炉)では、形状に関して前処理が重要とされ、ペレット状化が好まれ、一体物やプレス品は不適切とされている。
Next, an embodiment of the present invention using the industrial waste treatment apparatus will be described.
First, the body 21 of the rotary kiln 2 is rotated, the first burner 23 is ignited, and the inside of the body 21 is heated to an appropriate temperature of 1400 ° C. or less, for example, 1350 ° C.
Next, for example, a press crushed body (industrial waste W2) of a waste car is transported to the base of the rotary kiln by the carrying-in mechanism 12 with a conveyor, and is introduced into the body 21 from the inlet 22. In the case of a rotary kiln system, the shape of the press crushed material does not matter in particular, and any crushed material can be melted as long as it can be charged as a powder or as an integrated material. In other melting furnace systems (eg, gasification melting furnaces), pretreatment is important with respect to the shape, pelletization is preferred, and integral and pressed products are considered unsuitable.

 このとき、産業廃棄物W2の導入量に対応して、予め計算された量の消石灰をスラグ溶融剤として同時に搬入機構12から導入する。導入する消石灰の量は、溶融によって生成するスラグSの溶融温度が1400℃以下、例えば1350℃になるように、スラグSの塩基度(CaO/SiO重量比)を調整できる量であって、予めスラグSの組成分析によって計算される。 At this time, an amount of slaked lime calculated in advance corresponding to the introduced amount of the industrial waste W2 is simultaneously introduced from the loading mechanism 12 as a slag melting agent. The amount of slaked lime to be introduced is an amount that can adjust the basicity (CaO / SiO 2 weight ratio) of the slag S so that the melting temperature of the slag S generated by melting is 1400 ° C. or less, for example, 1350 ° C. It is calculated in advance by a composition analysis of the slag S.

 消石灰と共にロータリーキルン2内に導入された産業廃棄物W2は、第1バーナー23の熱風によって溶融され、可燃物は分解されてガス化し、一方、金属を含む不燃性物質はロータリーキルン内の前記温度によって溶融状態または半溶融状態の流動体Fとなる。 The industrial waste W2 introduced into the rotary kiln 2 together with slaked lime is melted by the hot air of the first burner 23, and combustibles are decomposed and gasified, while non-combustible substances including metals are melted by the temperature in the rotary kiln. The fluid F is in a state or a semi-molten state.

 生成したガス成分はロータリーキルン2の開放端部25から2次燃焼室3に送られ、この2次燃焼室3で、更に第2バーナー34からの熱風と空気供給管35からの空気の供給を受けて高温で燃焼され、例えばダイオキシンや悪臭物質などが分解され、排出口33から燃焼ガスGとして後処理工程に向けて排出される。 The generated gas component is sent from the open end 25 of the rotary kiln 2 to the secondary combustion chamber 3 where the secondary combustion chamber 3 receives hot air from the second burner 34 and air supply from the air supply pipe 35. For example, dioxin and odorous substances are decomposed and discharged from a discharge port 33 as a combustion gas G toward a post-processing step.

 ロータリーキルン2内に形成された前記流動体Fは、胴部21の傾斜に沿って流動しながら、この間に消石灰の添加によって塩基度が上昇して流動性が増したスラグSと、Feを主成分とし他の金属を含む溶融金属Mとが比重差によって分離する。この溶融金属Mと溶融スラグSは、互いに分離した状態でロータリーキルンの開放端部25から流下し、水砕ピット4の水槽41内で冷却され破砕され砕塊Rとなる。このとき、金属とスラグとは別の砕塊として得られる。得られた砕塊Rはコンベア42によって搬出される。
 得られた砕塊Rは、例えば磁気選鉱装置などによって、金属の砕塊とスラグの砕塊とに容易に分別することができる。
The fluid F formed in the rotary kiln 2 flows along the slope of the body portion 21 while the slag S whose basicity is increased by the addition of slaked lime and the fluidity is increased, and Fe as a main component. And the molten metal M containing other metals is separated by a difference in specific gravity. The molten metal M and the molten slag S flow down from the open end 25 of the rotary kiln while being separated from each other, and are cooled and crushed in the water tank 41 of the granulation pit 4 to form a crushed mass R. At this time, the metal and the slag are obtained as separate lumps. The obtained crushed mass R is carried out by the conveyor 42.
The obtained crushed mass R can be easily separated into crushed metal lumps and slag crushed mass by, for example, a magnetic separation device.

(試験例)
 図1に示した産業廃棄物処理装置において、産業廃棄物W2として廃自動車のプレス解砕体を用い、スラグ溶融剤として消石灰を用い、このときの塩基度を表1に示すように種々に変化させて、溶融温度1350℃で溶融を行った。磁気選鉱装置によって金属砕塊を分別し、各塩基度におけるCu回収率を測定した。結果を表1に示す。
(Test example)
In the industrial waste treatment apparatus shown in FIG. 1, a press crushed body of an end-of-life vehicle is used as the industrial waste W2, slaked lime is used as the slag melting agent, and the basicity at this time varies as shown in Table 1. Then, melting was performed at a melting temperature of 1350 ° C. The metal lumps were separated by a magnetic beneficiation apparatus, and the Cu recovery at each basicity was measured. Table 1 shows the results.

Figure 2004090004
Figure 2004090004

 表1から明らかなように、スラグ溶融剤を添加してスラグの塩基度を0.35〜1.35の範囲内で変化させた場合には、いずれも90重量%以上の高いCu回収率が得られた。これに比べ、塩基度が0.35未満の場合は、Cu回収率が低く、溶融炉内において溶融金属とスラグとが十分に分離していないことを示している。 As is clear from Table 1, when the basicity of the slag was changed within the range of 0.35 to 1.35 by adding the slag melting agent, a high Cu recovery of 90% by weight or more was obtained. Obtained. In contrast, when the basicity is less than 0.35, the recovery rate of Cu is low, indicating that the molten metal and the slag are not sufficiently separated in the melting furnace.

 金属含有産業廃棄物を溶融炉内に導入して溶融するに際して、この溶融によって溶出する溶融金属をスラグから分離して回収することができるとともに、溶融炉の熔損を防止して溶融炉の耐用期間を延長することができる。 When metal-containing industrial waste is introduced into a melting furnace and melted, the molten metal eluted by this melting can be separated and recovered from the slag, and the melting furnace can be prevented from being melted and serviceable. The period can be extended.

本発明の産業廃棄物処理装置の一実施形態を示す断面図である。It is a sectional view showing one embodiment of an industrial waste disposal device of the present invention. 従来の産業廃棄物処理装置の一例を示す断面図である。It is sectional drawing which shows an example of the conventional industrial waste processing apparatus.

符号の説明Explanation of reference numerals

 1,11,12:搬入機構
 2:ロータリーキルン式溶融炉
 21:胴部
 22:導入口
 23:第1バーナー
 24;回転機構
 25:開放端部
 3:2次燃焼室
 4:水砕ピット(冷却破砕手段)
 41:水槽
 42:コンベア
 W1:産業廃棄物
 W2:産業廃棄物またはその解砕物
 F:流動体
 S:スラグ
 M:溶融金属
 R:砕塊
1, 11, 12: Loading mechanism 2: Rotary kiln type melting furnace 21: Body 22: Inlet 23: First burner 24; Rotating mechanism 25: Open end 3: Secondary combustion chamber 4: Granulation pit (cooling and crushing) means)
41: Water tank 42: Conveyor W1: Industrial waste W2: Industrial waste or its crushed material F: Fluid S: Slag M: Molten metal R: Crushed lump

Claims (6)

金属含有産業廃棄物を溶融するロータリーキルン式溶融炉と、
 該溶融炉内で生成された溶融金属および溶融スラグからなる流動体を冷却、破砕する冷却破砕手段とを備える産業廃棄物処理装置であって、
 前記産業廃棄物およびスラグ溶融剤を前記溶融炉内に導入する搬入機構を備え、
 前記スラグ溶融剤を前記溶融炉内へ導入することによって、該溶融炉内における前記産業廃棄物の溶融により生成するスラグの溶融温度が1400℃以下となるようにこのスラグの塩基度(CaO/SiO重量比)を調整し、前記溶融スラグの流動性を増大させることにより、前記溶融炉内で前記溶融金属と前記溶融スラグとをこれらの比重差により分離する構成とされ、
 前記冷却破砕手段は、前記溶融炉から排出される前記流動体を冷却し破砕する水槽を備え、
 前記溶融金属と前記溶融スラグとを互いが分離した状態で前記溶融炉から流下させ、前記水槽内で冷却破砕し、金属とスラグとを別の砕塊として得る構成とされたことを特徴とする産業廃棄物処理装置。
A rotary kiln type melting furnace for melting metal-containing industrial waste,
Cooling and crushing means for cooling a fluid comprising molten metal and molten slag generated in the melting furnace, comprising:
A carry-in mechanism for introducing the industrial waste and the slag melt into the melting furnace,
By introducing the slag melting agent into the melting furnace, the basicity of the slag (CaO / SiO 2) is adjusted so that the melting temperature of the slag generated by melting the industrial waste in the melting furnace is 1400 ° C. or less. 2 weight ratio), and by increasing the fluidity of the molten slag, the molten metal and the molten slag are separated in the melting furnace by a difference in their specific gravities,
The cooling and crushing means includes a water tank for cooling and crushing the fluid discharged from the melting furnace,
The molten metal and the molten slag are flowed down from the melting furnace in a state where they are separated from each other, cooled and crushed in the water tank, and the metal and the slag are obtained as another crushed mass. Industrial waste treatment equipment.
請求項1記載の産業廃棄物処理装置において、
 前記冷却破砕手段により得られた砕塊を金属の破塊とスラグの破塊とに分別する磁気選鉱装置を備えることを特徴とする産業廃棄物処理装置。
The industrial waste treatment apparatus according to claim 1,
An industrial waste treatment apparatus, comprising: a magnetic ore separation device that separates crushed lumps obtained by the cooling crushing means into metal crushed pieces and slag crushed pieces.
前記スラグの塩基度を、0.35〜1.35の範囲内に調整することを特徴とする請求項1または2に記載の産業廃棄物処理装置。 The industrial waste treatment apparatus according to claim 1 or 2, wherein the basicity of the slag is adjusted within a range of 0.35 to 1.35. 前記スラグの塩基度を、CaOを含むスラグ溶融剤の添加により調整することを特徴とする請求項1〜請求項3のいずれかに記載の産業廃棄物処理装置。 The industrial waste treatment apparatus according to any one of claims 1 to 3, wherein the basicity of the slag is adjusted by adding a slag flux containing CaO. 前記溶融炉内に、C(炭素)を含む還元剤を添加することを特徴とする請求項1〜請求項4のいずれかに記載の産業廃棄物処理装置。 The industrial waste treatment apparatus according to any one of claims 1 to 4, wherein a reducing agent containing C (carbon) is added into the melting furnace. 前記溶融炉内の少なくとも前記スラグが接触する部分を、MgOを主成分とする塩基性マグネシア系耐火材で被覆することを特徴とする請求項1〜請求項5のいずれかに記載の産業廃棄物処理装置。
The industrial waste according to any one of claims 1 to 5, wherein at least a portion of the melting furnace in contact with the slag is coated with a basic magnesia-based refractory material containing MgO as a main component. Processing equipment.
JP2003354311A 2003-10-14 2003-10-14 Industrial waste treatment equipment Expired - Lifetime JP4216160B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP2003354311A JP4216160B2 (en) 2003-10-14 2003-10-14 Industrial waste treatment equipment

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP2003354311A JP4216160B2 (en) 2003-10-14 2003-10-14 Industrial waste treatment equipment

Related Parent Applications (1)

Application Number Title Priority Date Filing Date
JP27539299A Division JP3527149B2 (en) 1999-09-28 1999-09-28 Industrial waste treatment method

Publications (2)

Publication Number Publication Date
JP2004090004A true JP2004090004A (en) 2004-03-25
JP4216160B2 JP4216160B2 (en) 2009-01-28

Family

ID=32064626

Family Applications (1)

Application Number Title Priority Date Filing Date
JP2003354311A Expired - Lifetime JP4216160B2 (en) 2003-10-14 2003-10-14 Industrial waste treatment equipment

Country Status (1)

Country Link
JP (1) JP4216160B2 (en)

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2007120859A (en) * 2005-10-27 2007-05-17 Hitachi Metals Ltd Evaporation preventing device of combustor slag collection/water sealing portion
JP2008534781A (en) * 2005-04-01 2008-08-28 テキント コンパニア テクニカ インテルナツィオナレ ソシエタ ペル アチオニ Method and apparatus for secondary refining slag regeneration and recycling in steelmaking process by electric arc furnace
JP2015147985A (en) * 2014-02-07 2015-08-20 Jx日鉱日石金属株式会社 Apparatus and method for recovering/treating valuable metal

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2008534781A (en) * 2005-04-01 2008-08-28 テキント コンパニア テクニカ インテルナツィオナレ ソシエタ ペル アチオニ Method and apparatus for secondary refining slag regeneration and recycling in steelmaking process by electric arc furnace
JP2007120859A (en) * 2005-10-27 2007-05-17 Hitachi Metals Ltd Evaporation preventing device of combustor slag collection/water sealing portion
JP2015147985A (en) * 2014-02-07 2015-08-20 Jx日鉱日石金属株式会社 Apparatus and method for recovering/treating valuable metal

Also Published As

Publication number Publication date
JP4216160B2 (en) 2009-01-28

Similar Documents

Publication Publication Date Title
RU2398895C2 (en) PROCEDURE FOR ROASTING MATERIAL CONTAINING AT LEAST ONE METAL FROM GROUP INCLUDING V OR Mo, OR Ni AND ROTATING FURNACE FOR THIS MATERIAL ROASTING
WO2019042157A1 (en) Comprehensive resourceful treatment system for electronic waste and method therefor
CN201273767Y (en) Multifunctional industrial furnace and continuous smelting system comprising the industrial furnace
JP2010111941A (en) Method for producing ferrovanadium
CN1539024A (en) Method for direct metal making by microwave energy
CN109306407A (en) A kind of device and method that metallurgy dedusting ash containing zinc is administered and utilized
KR19990008192A (en) Method for recovering metal from iron oxide containing mass
WO2009114155A2 (en) Feed material compostion and handling in a channel induction furnace
JP5224490B2 (en) Processing method of smoke from furnace
WO2009114156A2 (en) Feed material compostion and handling in a channel induction furnace
WO2009114159A2 (en) Feed material compostion and handling in a channel induction furnace
JP4216160B2 (en) Industrial waste treatment equipment
WO2009114157A2 (en) Feed material compostion and handling in a channel induction furnace
JP3527149B2 (en) Industrial waste treatment method
JP2000045008A (en) Production of reduced metal
JP2005126732A (en) Smelting-reduction method for material containing metallic oxide, and smelting-reduction apparatus
JP3365557B2 (en) Method for melting oxide-based slag and combustion residue, and apparatus for performing the method
RU2461776C1 (en) Non-waste thermal processing method of solid public wastes, and unit for its implementation
JP2009063286A (en) Waste treatment method, metal manufacturing method and metal
WO2006086874A1 (en) Converting spent potliners into a glass frit
JP2002241820A (en) Smelting reduction method for iron oxide using rotary kiln
JP3451901B2 (en) Operating method of mobile hearth furnace
JP6793869B1 (en) Waste melting treatment method, waste melting slag powder and its manufacturing method
JP2001221418A (en) Furnace for processing waste battery cell
RU2710250C1 (en) Method of carbon-free selective extraction of zinc and lead from dust of electric steel making and device for its implementation

Legal Events

Date Code Title Description
A521 Request for written amendment filed

Free format text: JAPANESE INTERMEDIATE CODE: A523

Effective date: 20031105

A621 Written request for application examination

Free format text: JAPANESE INTERMEDIATE CODE: A621

Effective date: 20060926

A977 Report on retrieval

Free format text: JAPANESE INTERMEDIATE CODE: A971007

Effective date: 20081016

TRDD Decision of grant or rejection written
A01 Written decision to grant a patent or to grant a registration (utility model)

Free format text: JAPANESE INTERMEDIATE CODE: A01

Effective date: 20081028

A01 Written decision to grant a patent or to grant a registration (utility model)

Free format text: JAPANESE INTERMEDIATE CODE: A01

A61 First payment of annual fees (during grant procedure)

Free format text: JAPANESE INTERMEDIATE CODE: A61

Effective date: 20081105

R150 Certificate of patent or registration of utility model

Ref document number: 4216160

Country of ref document: JP

Free format text: JAPANESE INTERMEDIATE CODE: R150

Free format text: JAPANESE INTERMEDIATE CODE: R150

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

Free format text: PAYMENT UNTIL: 20111114

Year of fee payment: 3

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

Free format text: PAYMENT UNTIL: 20111114

Year of fee payment: 3

S531 Written request for registration of change of domicile

Free format text: JAPANESE INTERMEDIATE CODE: R313531

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

Free format text: PAYMENT UNTIL: 20111114

Year of fee payment: 3

R350 Written notification of registration of transfer

Free format text: JAPANESE INTERMEDIATE CODE: R350

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

Free format text: PAYMENT UNTIL: 20111114

Year of fee payment: 3

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

Free format text: PAYMENT UNTIL: 20121114

Year of fee payment: 4

R250 Receipt of annual fees

Free format text: JAPANESE INTERMEDIATE CODE: R250

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

Free format text: PAYMENT UNTIL: 20131114

Year of fee payment: 5

R250 Receipt of annual fees

Free format text: JAPANESE INTERMEDIATE CODE: R250

R250 Receipt of annual fees

Free format text: JAPANESE INTERMEDIATE CODE: R250

R250 Receipt of annual fees

Free format text: JAPANESE INTERMEDIATE CODE: R250

R250 Receipt of annual fees

Free format text: JAPANESE INTERMEDIATE CODE: R250

R250 Receipt of annual fees

Free format text: JAPANESE INTERMEDIATE CODE: R250

R250 Receipt of annual fees

Free format text: JAPANESE INTERMEDIATE CODE: R250

R250 Receipt of annual fees

Free format text: JAPANESE INTERMEDIATE CODE: R250

EXPY Cancellation because of completion of term