JP2002048322A - Melting processing method and melting processing furnace for waste - Google Patents

Melting processing method and melting processing furnace for waste

Info

Publication number
JP2002048322A
JP2002048322A JP2000237472A JP2000237472A JP2002048322A JP 2002048322 A JP2002048322 A JP 2002048322A JP 2000237472 A JP2000237472 A JP 2000237472A JP 2000237472 A JP2000237472 A JP 2000237472A JP 2002048322 A JP2002048322 A JP 2002048322A
Authority
JP
Japan
Prior art keywords
furnace
waste
melting
ceramics
molded body
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Withdrawn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
JP2000237472A
Other languages
Japanese (ja)
Inventor
Mitsuhiko Shiraishi
光彦 白石
Morihiro Osada
守弘 長田
Hidemi Osano
秀実 小佐野
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
Original Assignee
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 Nippon Steel Corp filed Critical Nippon Steel Corp
Priority to JP2000237472A priority Critical patent/JP2002048322A/en
Publication of JP2002048322A publication Critical patent/JP2002048322A/en
Withdrawn legal-status Critical Current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
    • Y02EREDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
    • Y02E20/00Combustion technologies with mitigation potential
    • Y02E20/12Heat utilisation in combustion or incineration of waste
    • 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
    • Y02EREDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
    • Y02E20/00Combustion technologies with mitigation potential
    • Y02E20/34Indirect CO2mitigation, i.e. by acting on non CO2directly related matters of the process, e.g. pre-heating or heat recovery
    • 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
    • Y02PCLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
    • Y02P10/00Technologies related to metal processing
    • Y02P10/25Process efficiency

Landscapes

  • Waste-Gas Treatment And Other Accessory Devices For Furnaces (AREA)
  • Furnace Details (AREA)
  • Incineration Of Waste (AREA)
  • Processing Of Solid Wastes (AREA)
  • Manufacture And Refinement Of Metals (AREA)
  • Gasification And Melting Of Waste (AREA)
  • Vertical, Hearth, Or Arc Furnaces (AREA)

Abstract

PROBLEM TO BE SOLVED: To provide a melting processing method and a melting processing furnace for waste in which upon directly melting waste the processing cost is reduced. SOLUTION: Air that is rich in air or oxygen from tuyeres 3, 4 at a single stage or a plurality of stages is blown into previously heat, dry, and thermally decompose waste, and thereafter alternating electric power is supplied to a heating coil 10 disposed on an outer periphery at a lower portion in the furnace, whereby a molded workpiece obtained by coating with ceramics graphite or cokes previously disposed at a lower portion in the furnace, or a molded workpiece obtained by blending carbon powder and ceramics, or a molded workpiece of electrically conductive ceramics is induction-heated to melt thermal decomposition residues in the waste.

Description

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

【0001】[0001]

【発明の属する技術分野】本発明は、都市ごみ、産業廃
棄物、汚泥、最終処分場に埋め立てた廃棄物を掘り起こ
した廃棄物等の廃棄物を直接溶融してスラグを製造する
廃棄物の溶融処理方法および廃棄物処理炉に関するもの
である。本発明の方法によって製造したスラグは土木資
材、道路舗装材、コンクリート骨材等に利用することが
可能である。
TECHNICAL FIELD The present invention relates to the melting of waste such as municipal solid waste, industrial waste, sludge, and waste produced by digging up waste landfilled at a final disposal site to produce slag. The present invention relates to a treatment method and a waste treatment furnace. The slag produced by the method of the present invention can be used for civil engineering materials, road pavement materials, concrete aggregates and the like.

【0002】[0002]

【従来の技術】現状は、大半の廃棄物は焼却方式で処理
されているが、焼却方式では焼却灰の処分場を必要とす
る等の欠点がある。特に大都市圏では焼却灰の処分場の
確保が困難であり、従って廃棄物を焼却炉で焼却した焼
却灰を更に溶融して減容化する方法、または廃棄物を直
接溶融して減容化する方法等の必要性が高まっている。
2. Description of the Related Art At present, most waste is treated by an incineration method, but the incineration method has a drawback that a disposal site for incinerated ash is required. Particularly in metropolitan areas, it is difficult to secure a disposal site for incinerated ash.Therefore, a method of further melting and reducing the volume of incinerated ash incinerated with waste, or reducing the volume by directly melting the waste There is a growing need for methods to do so.

【0003】廃棄物の焼却灰を溶融する方法として、ア
ーク炉で溶融する方法や誘導加熱で溶融する方法が特公
平4−81084号公報、特開平11−211032号
公報に開示されている。
[0003] As a method of melting incinerated ash of waste, a method of melting in an arc furnace and a method of melting by induction heating are disclosed in Japanese Patent Publication No. 4-81084 and Japanese Patent Application Laid-Open No. 11-211032.

【0004】廃棄物を焼却することなくシャフト炉で直
接溶融する方法が特公昭60−11766号公報に開示
されている。また、導電性の溶融用容器を誘導加熱する
ことにより、廃棄物を焼却、溶融する方法が特開平6−
273951号公報に開示されている。
A method for directly melting waste in a shaft furnace without incineration is disclosed in Japanese Patent Publication No. 60-11766. Further, a method of incinerating and melting waste by inductively heating a conductive melting container is disclosed in Japanese Patent Application Laid-Open No. H06-26,004.
No. 273951.

【0005】[0005]

【発明が解決しようとする課題】しかしながら、前者の
焼却灰を溶融する方式は、廃棄物を一旦焼却した後に溶
融するため二段階の処理が必要であり、焼却炉から排出
された焼却灰を冷却する設備、溶融炉まで搬送する設備
等多くの設備を設置しなければならない。
However, the former method of melting incinerated ash requires two-stage treatment because the waste is once incinerated and then melted, and the incinerated ash discharged from the incinerator is cooled. Many facilities must be installed, such as a facility for transporting materials to the melting furnace.

【0006】また後者のシャフト炉で直接溶融する方法
は、コークス等の燃料が必要なこと等の問題がある。導
電性の溶融用容器を誘導加熱する方法では、溶融物の伝
熱が非常に悪く熱が伝わらないため、発熱体である容器
から離れた中央部は温度が低く均一に溶融できない。必
然的に容器の直径に限界があり、1日に処理できる廃棄
物の量は数トンが限界である。
Further, the latter method of directly melting in a shaft furnace has a problem that a fuel such as coke is required. In the method of inductively heating a conductive melting container, the heat transfer of the molten material is so bad that no heat is transmitted. Inevitably, the diameter of the container is limited, and the amount of waste that can be treated in a day is limited to several tons.

【0007】本発明は上記の問題点を解決するために、
廃棄物を焼却することなく直接溶融するに当たり、処理
費用を低減するとともに、大量に排出される廃棄物の実
情に合った溶融処理方法を提供することを目的とする。
The present invention has been made to solve the above problems.
It is an object of the present invention to provide a melting treatment method suitable for the actual situation of waste discharged in large quantities, while reducing the processing cost in directly melting waste without incineration.

【0008】[0008]

【課題を解決するための手段】本発明は、上記の課題を
解決するため、単段または複数段の羽口から空気または
酸素を富化した空気を吹き込み装入された廃棄物を還元
燃焼せしめ、しかして廃棄物を予熱、乾燥熱分解させて
ガス化すると共に、熱分解残渣を炉下部の外周に設置し
た加熱コイルに交番電流を通電することにより炉内下部
に予め配置した黒鉛またはコークスをセラミックスで被
覆した成形体、または炭素粉をセラミックスと混合して
成形した成形体、または導電性セラミックスの成形体を
誘導加熱し、廃棄物の熱分解残渣を溶融処理する方法お
よびその装置である。
SUMMARY OF THE INVENTION In order to solve the above-mentioned problems, the present invention reduces and combusts waste that has been charged by blowing air or oxygen-enriched air from single or multiple-stage tuyeres. Thus, the waste is preheated, gasified by dry pyrolysis, and the pyrolysis residue is graphite or coke previously placed in the lower part of the furnace by applying an alternating current to a heating coil installed on the outer periphery of the lower part of the furnace. A method and apparatus for subjecting a molded body coated with ceramics, a molded body formed by mixing carbon powder with ceramics, or a molded body of conductive ceramics to induction heating to melt-process pyrolysis residues of waste.

【0009】[0009]

【発明の実施の形態】本発明について詳細に説明する。
溶融炉はシャフト炉で構成され、炉本体は上部から下部
に向かって、予熱帯、乾燥帯、熱分解帯、溶融帯を形成
しており、溶融炉上部から供給した廃棄物は、炉内を降
下する過程で順次予熱、乾燥、熱分解して、ガス化成分
をガス化させた後熱分解残渣を炉底部で溶融する。予
熱、乾燥、熱分解の加熱源としては、炉本体下部から空
気または酸素を富化した空気を吹き込み、廃棄物中の可
燃物質を部分的に燃やすことで還元燃焼させ、この時発
生する高温ガスが炉内を上昇して、炉上部から供給され
た廃棄物を予熱、乾燥、熱分解する。
DETAILED DESCRIPTION OF THE INVENTION The present invention will be described in detail.
The melting furnace is composed of a shaft furnace, and the furnace body forms a pre-tropical zone, a drying zone, a pyrolysis zone, and a melting zone from the upper part to the lower part, and the waste supplied from the upper part of the melting furnace passes through the furnace. In the process of descending, it is preheated, dried and thermally decomposed sequentially to gasify gasification components, and then the pyrolysis residue is melted at the furnace bottom. As a heating source for preheating, drying, and pyrolysis, air or oxygen-enriched air is blown in from the lower part of the furnace body, and combustible substances in waste are partially burned to reduce and burn. Rises inside the furnace to preheat, dry and pyrolyze the waste supplied from the furnace top.

【0010】一方溶融帯では、炉本体下部に予め黒鉛ま
たはコークスをセラミックスで被覆した成形体、または
炭素粉をセラミックスと混合して成形した成形体、また
は導電性セラミックスの成形体を配置しておき、該成形
体を誘導加熱した熱と、廃棄物自身が熱分解残渣となる
過程で昇温された熱を足し合わせた熱で熱分解残渣を溶
融する。この場合の熱分解残渣とは可燃物が熱分解して
できた残渣の他に、瓦礫類、陶磁器類、ビン類、金属類
等の不燃物も含む。誘導加熱に使用する電気は、廃棄物
中の可燃物質を部分的に燃やし還元燃焼させることで可
燃性の熱分解ガスを発生させ、溶融炉の後段に設けた二
次燃焼炉で完全燃焼し、その次に設けたボイラと発電機
で回収した電気エネルギーを使用する。
On the other hand, in the melting zone, a molded body in which graphite or coke is coated with ceramics in advance, a molded body formed by mixing carbon powder with ceramics, or a molded body made of conductive ceramics is arranged in the lower part of the furnace body. Then, the pyrolysis residue is melted by the heat obtained by adding the heat of induction heating of the molded body and the heat raised in the process of turning the waste itself into the pyrolysis residue. The pyrolysis residue in this case includes non-combustible substances such as rubble, ceramics, bottles, and metals, in addition to the residue formed by the pyrolysis of combustibles. Electricity used for induction heating generates combustible pyrolysis gas by partially burning and reducing combustion of combustible substances in waste, and complete combustion in the secondary combustion furnace provided at the latter stage of the melting furnace, The electric energy recovered by the boiler and generator provided next is used.

【0011】黒鉛またはコークスをセラミックスで被覆
した成形体、または炭素粉をセラミックスと混合して成
形した成形体とすることで、発熱体である黒鉛やコーク
スが燃焼ガスと接触して消耗することを防止することが
できる。炭素粉としでは、定型炭素でも不定形炭素でも
よい。また、発熱体として導電性セラミックを使用する
こともでき、燃焼ガスとの接触による消耗は少ない。導
電性セラミックスとしては、炭化珪素質、珪化モリブデ
ン質、炭素質、ランタンクロマイト質等が使用できる。
また、黒鉛またはコークスを被覆するセラミックス、ま
たは炭素粉と混合するセラミックスは、市販の炭化珪素
質、アルミナ質、マグネシア質等やこれらの複合材料と
したセラミックスでよく、当然導電性セラミックスを用
いても良い。但し、発熱体として導電性セラミックスを
使用する場合は、温度により電気抵抗値が変化し、多く
の場合低温で抵抗値が高く、高温で抵抗値が下がる傾向
があるため溶融炉の立ち上げ初期の昇温に若干時間が余
計にかかる場合があるので注意が必要である。
By forming a molded body in which graphite or coke is coated with ceramics or a molded body in which carbon powder is mixed with ceramics, graphite or coke, which is a heating element, is consumed by contact with a combustion gas. Can be prevented. In the case of carbon powder, regular carbon or irregular carbon may be used. In addition, a conductive ceramic can be used as the heating element, and is less consumed by contact with the combustion gas. As the conductive ceramic, silicon carbide, molybdenum silicide, carbon, lanthanum chromite, or the like can be used.
Further, the ceramic to be coated with graphite or coke, or the ceramic to be mixed with the carbon powder may be a commercially available ceramic such as silicon carbide, alumina, magnesia, or a composite material of these, and naturally a conductive ceramic may be used. good. However, when conductive ceramics are used as the heating element, the electrical resistance changes depending on the temperature, and in many cases, the resistance tends to increase at low temperatures and decrease at high temperatures. Care must be taken because the heating may take some extra time.

【0012】炉内下部に配置する成形体の形状として
0.008m以下の塊とし、炉内下部に充填すること
で、発熱体のみならず火格子としての役割もし、溶融物
と未溶融物を効率的に分離するので有効利用に適した溶
融物が製造できる。塊は、球形に近い物であると、空隙
が均一になりやすく好ましい。0.008mを越えた
塊の成形体を用いた場合は、空隙から末燃分が排出され
る場合があるため好ましくない。
[0012] and 0.008 m 3 or less of the mass as the shape of the molded body disposed below the furnace, by filling in the lower furnace, the role if melt and the unmelted material as grate not heating element only Is efficiently separated, so that a melt suitable for effective use can be produced. It is preferable that the lump has a shape close to a spherical shape because the voids can be uniform. It is not preferable to use a compact having a mass exceeding 0.008 m 3 , since end-burning components may be discharged from the voids.

【0013】炉内下部に配置する成形体のその他の形状
としては、角柱状とし、炉内下部に格子状に積み上げる
ことで、前記同様火格子としての役割をし、溶融物と未
溶融物を効率的に分離するので有効利用に適した溶融物
が製造できる。
[0013] As another shape of the molded body disposed in the lower part of the furnace, a prismatic shape is formed, and by stacking it in a lattice shape in the lower part of the furnace, it functions as a fire grate as described above, and the molten material and the unmolten material are separated. Since it separates efficiently, a melt suitable for effective use can be produced.

【0014】本発明は、配置する成形体を導電性とする
ことで、発熱した成形体が熱分解残渣と直接接触して溶
融するため、容器を誘導加熱するのとは異なり炉の直径
に制限がなく、廃棄物の1日当たりの処理量は数百トン
も可能である。また、容器の発熱がないため、耐火物の
損耗も少ない。
According to the present invention, since the molded body to be arranged is made conductive, the heated molded body is brought into direct contact with the pyrolysis residue and melts. And hundreds of tons of waste per day are possible. Further, since there is no heat generation in the container, wear of the refractory is small.

【0015】炉内を還元雰囲気にすると、重金属類のよ
うな物質は還元揮発し排ガス側に移行する。そこで、本
発明は、炉内にコークスを装入して炉内を還元雰囲気と
し、重金属等を揮発させて有害物質の含有が極めて少な
い溶融物とすることで、安全な溶融物を製造できる。ま
た、炭化珪素質等の炭素を含んだセラミックスを使用す
る場合、炉内にコークスを装入し還元雰囲気にすると、
より消耗はなくなる。一方、揮発し排ガス側に移行した
重金属類は、最終的に元の廃棄物よりも濃縮された状態
で集塵機で捕集され、山元還元も可能である。
When the inside of the furnace is set to a reducing atmosphere, substances such as heavy metals are reduced and volatilized and transferred to the exhaust gas side. Therefore, according to the present invention, a safe melt can be produced by charging coke into the furnace, setting the furnace in a reducing atmosphere, and volatilizing heavy metals and the like into a melt containing very little harmful substance. Also, when using a ceramic containing carbon such as silicon carbide, if coke is charged into the furnace and the atmosphere is reduced,
There is no more wear. On the other hand, the heavy metals volatilized and moved to the exhaust gas side are finally collected in a dust collector in a state where they are more concentrated than the original waste, and yamamoto can be reduced.

【0016】従来の焼却灰を誘導加熱する技術では、廃
棄物の焼却灰を対象としているため、溶融炉内の構成が
本発明とは異なる。従来技術では、焼却灰を溶融してい
るため、別に廃棄物を焼却するための焼却炉を設置する
必要がある。本発明では、廃棄物を事前に焼却炉で焼却
処理することなく、予熱帯、乾燥帯、熱分解帯を有する
シャフト部を設けることで廃棄物を直接、一つのプロセ
スで溶融処理を行うことができる。また、従来技術では
溶融炉内に空気を供給して、焼却灰の未燃分を酸化燃焼
させているが、本発明は、廃棄物を部分燃焼させて炉内
を還元雰囲気とし、可燃性の熱分解ガスを発生させるこ
とで、溶融炉の後段に設けた二次燃焼炉でガスを補助燃
料なしに容易に完全燃焼でき、その結果、次に設けたボ
イラと発電機で電気エネルギーを回収することが可能に
なる。本発明は、廃棄物の溶融熱源としては廃棄物の持
つ発熱量を直接、および回収した電気の形態で利用する
ことができるという効果を有する。
In the conventional technology for inductively heating incinerated ash, since the incinerated ash of waste is targeted, the configuration inside the melting furnace is different from that of the present invention. In the prior art, since incinerated ash is melted, it is necessary to install an incinerator for incinerating waste separately. In the present invention, the waste can be directly melted in one process by providing a shaft portion having a pre-tropical zone, a drying zone, and a pyrolysis zone without incinerating the waste in an incinerator in advance. it can. In the prior art, air is supplied into the melting furnace to oxidize and burn the unburned portion of the incinerated ash.However, the present invention partially burns the waste to make the furnace a reducing atmosphere, By generating the pyrolysis gas, the gas can be easily and completely burned without auxiliary fuel in the secondary combustion furnace provided at the latter stage of the melting furnace, and as a result, electric energy is recovered by the boiler and generator provided next. It becomes possible. The present invention has an effect that the calorific value of the waste can be used directly and in the form of recovered electricity as a heat source for melting the waste.

【0017】[0017]

【実施例】実施例1 廃棄物を溶融処理する実施例として、炉内下部に予め黒
鉛をセラミックスで被覆し、0.0003mの体積で
球状の成形体を炉内下部に充填した溶融処理装置で溶融
処理する場合を図1に示す。
As an example of the EXAMPLE 1 Waste melt processing, the advance graphite in the lower furnace are coated with ceramics, melting treatment apparatus was charged to furnace bottom a molded body of spherical volume of 0.0003 m 3 FIG. 1 shows the case where the melting process is performed.

【0018】該溶融処理装置は、シャフト炉1、廃棄物
装入装置2、上段羽口3、下段羽口4、シャフト部5、
朝顔部6、炉内下部7、ガス排出管8、スラグ排出口
9、加熱コイル10、高周波電源11、黒鉛をセラミッ
クスで被覆した球状の成形体12で構成される。
The melting apparatus includes a shaft furnace 1, a waste charging apparatus 2, an upper tuyere 3, a lower tuyere 4, a shaft part 5,
It is composed of a bosh section 6, a furnace lower part 7, a gas discharge pipe 8, a slag discharge port 9, a heating coil 10, a high-frequency power supply 11, and a spherical molded body 12 in which graphite is coated with ceramics.

【0019】図1において、廃棄物はシャフト炉1の炉
上部の廃棄物装入装置2から装入される。廃棄物として
は都市ごみを処理した。表1に溶融処理した都市ごみの
性状を示す。
In FIG. 1, waste is loaded from a waste loading device 2 at the upper part of a shaft furnace 1. Municipal waste was disposed of as waste. Table 1 shows the properties of the melted municipal solid waste.

【0020】[0020]

【表1】 シャフト炉1はシャフト部5、朝顔部6および炉内下部
7から構成され、朝顔部の周辺に設けられた上段羽口3
および炉内下部の周辺に設けられた下段羽口4から空気
を供給する。
[Table 1] The shaft furnace 1 is composed of a shaft portion 5, a bosh section 6, and a lower part 7 inside the furnace, and an upper tuyere 3 provided around the bosh section.
Air is supplied from a lower tuyere 4 provided around the lower part of the furnace.

【0021】廃棄物の処理は560Kg/h、黒鉛は廃
棄物の各々約1%および6%であり、空気は上段羽口か
ら200Nm/ h、下段羽口から400Nm/ h
を供給した。
The process 560 kg / h of waste graphite are each about 1% and 6% of the waste, 400 Nm 3 / h air from the upper tuyere 200 Nm 3 / h, from the lower tuyeres
Was supplied.

【0022】溶融炉に装入された廃棄物および黒鉛は炉
内で充填層を形成し、上段羽口3および下段羽口4から
吹き込まれた空気により、廃棄物の可燃分が燃焼する。
該燃焼ガスは溶融炉内を炉底部から上昇し、燃焼ガスの
顕熱により廃棄物を予熱、乾燥、熱分解する。廃棄物の
乾燥、熱分解の過程で発生した水蒸気、熱分解ガスおよ
び微細なダストはガス排出管8から排出される。
The waste and graphite charged into the melting furnace form a packed bed in the furnace, and the combustibles of the waste are burned by the air blown from the upper tuyere 3 and the lower tuyere 4.
The combustion gas rises in the melting furnace from the bottom of the furnace, and the waste is preheated, dried and thermally decomposed by the sensible heat of the combustion gas. Steam, pyrolysis gas and fine dust generated in the process of drying and pyrolysis of the waste are discharged from the gas discharge pipe 8.

【0023】一方、廃棄物の熱分解残渣は高温に加熱さ
れ炉内下部7へと下りていく。炉内下部の外周に設置し
た加熱コイル10に高周波電源11から交番電流を通電
して、炉内下部に充填した黒鉛をセラミックスで被覆し
た成形体12を誘導加熱し、該成形体12に廃棄物中の
熱分解残渣を接触させて溶融する。熱分解残渣は130
0℃から1750℃に加熱され溶融状態となって、スラ
グ排出口9から炉外へ排出される。
On the other hand, the thermal decomposition residue of the waste is heated to a high temperature and descends to the lower part 7 in the furnace. An alternating current is passed from a high-frequency power supply 11 to a heating coil 10 installed on the outer periphery of the lower part of the furnace to induction-heat a molded body 12 coated with graphite filled in the lower part of the furnace with ceramics. The pyrolysis residue inside is brought into contact and melted. Pyrolysis residue is 130
It is heated from 0 ° C. to 1750 ° C. to be in a molten state, and discharged from the slag discharge port 9 to the outside of the furnace.

【0024】誘導加熱の電力としては、ガス排出管から
排出されたガスを燃焼させ、その熱でボイラーで蒸気を
発生させて発電したものを利用した。このブロック図を
図2に示す。ガス排出管8から排出された排ガスは、二
次燃焼室14で排ガス中の未燃分を燃焼した後、この熱
でボイラー15で蒸気を発生させて発電機20で発電し
た電気を誘導加熱の電力として使用する。ボイラー15
を通過した後の排ガスは、排ガス冷却器16で排ガス温
度を下げた後、集塵機17でばい塵を集塵して煙突18
から排出する。
As the electric power for the induction heating, a gas generated by burning the gas discharged from the gas discharge pipe and generating steam by the boiler using the heat was used. This block diagram is shown in FIG. The exhaust gas discharged from the gas discharge pipe 8 burns unburned components in the exhaust gas in the secondary combustion chamber 14, generates steam in the boiler 15 with this heat, and generates electricity generated in the generator 20 by induction heating. Use as power. Boiler 15
After passing through the exhaust gas, the temperature of the exhaust gas is reduced by an exhaust gas cooler 16, dust is collected by a dust collector 17, and the
Discharged from

【0025】スラグ排出口9から排出された溶融状態の
スラグは水冷されて、砂状の細かい粒子となる。また、
溶融状態のスラグ中には溶融メタルが含まれているが、
メタルもスラグと同様に細かい粒子状となる。スラグは
インターロッキングブロック等のコンクリート2次製品
の骨材や土木資材などとして利用する。
The molten slag discharged from the slag discharge port 9 is water-cooled into fine sand-like particles. Also,
Slag in the molten state contains molten metal,
Metal also becomes fine particles like slag. Slag is used as aggregate or civil engineering material for secondary concrete products such as interlocking blocks.

【0026】図4は従来の技術のシャフト炉式方式の直
接溶融炉であり、図1と同一設備は同一記号で示した。
従来の方法で同一の廃棄物を処理した場合は、コークス
が廃棄物に対して6%程度必要であり、また酸素を下段
羽口45Nm程度富化して送風することが必要であ
り、炉下部にはコークスの充填層19をなす必要があっ
た。この従来の方式と比較して、実施例に示したように
本発明の方法ではコークス消費量及び酸素を低減でき
る。
FIG. 4 shows a conventional shaft furnace type direct melting furnace of the prior art, and the same equipment as in FIG. 1 is designated by the same symbol.
When the same waste is treated by the conventional method, coke needs to be about 6% of the waste, and it is necessary to enrich oxygen in the lower tuyere of about 45 Nm 3 and to blow air. Needed to form a packed layer 19 of coke. Compared with this conventional method, the method of the present invention can reduce coke consumption and oxygen as shown in the embodiments.

【0027】また、黒鉛をセラミックスで被覆した成形
体12の代わりに、コークスをセラミックスで被覆した
成形体、また炭素粉をセラミックスと混合して成形した
成形体、または導電性セラミックスの成形体を使用して
も同様の効果を得た。更に、炉内にコークスを装入し、
炉内の雰囲気を還元雰囲気にすることで、スラグに含有
する鉛の含有量を18mg/kgと、極微量にすること
ができた。
In place of the molded body 12 in which graphite is coated with ceramics, a molded body in which coke is coated with ceramics, a molded body formed by mixing carbon powder with ceramics, or a molded body made of conductive ceramics is used. The same effect was obtained. Furthermore, charge coke into the furnace,
By changing the atmosphere in the furnace to a reducing atmosphere, the content of lead contained in the slag could be reduced to a very small amount of 18 mg / kg.

【0028】処理対象の廃棄物として、都市ごみに焼却
灰を混合した廃棄物及び、都市ごみに汚泥を混合した廃
棄物をそれぞれ処理したが、前記と同様の効果が得られ
た。
As wastes to be treated, waste in which incinerated ash was mixed with municipal waste and waste in which sludge was mixed with municipal waste were respectively treated. The same effects as described above were obtained.

【0029】実施例2 実施例1で充填した球状の代わりに、予め黒鉛をセラミ
ックスで被覆した角柱状の成形体13を炉内下部に格子
状に積み上げた溶融処理装置を図3で示す。
EXAMPLE 2 FIG. 3 shows a melt processing apparatus in which prism-shaped compacts 13 previously coated with ceramics of graphite are stacked in a lattice at the lower part of the furnace, instead of the spheres filled in Example 1.

【0030】廃棄物は、実施例1と同様に加熱されて熱
分解残渣となり炉内下部7へと下りていく。炉内下部の
外周に設置した加熱コイル10に高周波電源11から交
番電流を通電して、炉内下部に積み上げた黒鉛をセラミ
ックスで被覆した角柱状の成形体13を誘導加熱し、高
温状態の成形体13に廃棄物の熱分解残渣を接触させて
溶融する。熱分解残渣は1300℃から1750℃に加
熱され溶融状態となって、スラグ排出口9から炉外へ排
出される。この結果、実施例1と同様の効果を得た。ま
た、黒鉛セラミックスで被覆した成形体13の代わり
に、コークスをセラミックスで被覆した成形体、または
炭素粉をセラミックスと混合して成形した成形体、導電
性セラミックスの成形体を使用しても同様の効果を得
た。
The waste is heated in the same manner as in the first embodiment to become a pyrolysis residue and goes down to the lower part 7 in the furnace. An alternating current is applied from a high-frequency power supply 11 to a heating coil 10 installed on the outer periphery of the lower part of the furnace to induce heating of a prism-shaped formed body 13 coated with ceramics stacked on the lower part of the furnace, thereby forming a high-temperature state. The pyrolysis residue of the waste is brought into contact with the body 13 and melted. The pyrolysis residue is heated from 1300 ° C. to 1750 ° C. to be in a molten state and discharged from the slag discharge port 9 to the outside of the furnace. As a result, the same effect as in Example 1 was obtained. In addition, instead of the molded body 13 coated with graphite ceramic, a molded body obtained by coating coke with ceramics, a molded body formed by mixing carbon powder with ceramics, or a molded body made of conductive ceramics is used in the same manner. The effect was obtained.

【0031】[0031]

【発明の効果】本発明によって、以下の効果を実現する
ことができる。
According to the present invention, the following effects can be realized.

【0032】1)廃棄物を焼却した後にアーク炉や誘導
加熱炉で焼却灰を溶融する方法と比較して、本発明の方
法は廃棄物を直接溶融でき、設備構成が簡素で経済的で
ある。さらに、焼却灰のハンドリングが不要であるばか
りでなく、焼却灰を一旦冷却してアーク炉で溶融する方
法と比較して熱効率がよい。
1) Compared with the method of melting incineration ash in an arc furnace or induction heating furnace after incineration of waste, the method of the present invention can directly melt waste, and the equipment configuration is simple and economical. . Furthermore, not only is the incineration ash unnecessary to be handled, but also the thermal efficiency is higher than the method of once cooling the incineration ash and melting it in an arc furnace.

【0033】2)廃棄物を焼却することなくシャフト炉
で直接溶融する場合、本発明においては黒鉛またはコー
クスをセラミックスで被覆した成形体、または炭素粉を
セラミックスと混合して成形した成形体、または導電性
セラミックスの成形体を誘導加熱して熱分解残渣を溶融
することによって、燃料の消費量を低減し、羽口から送
風する空気に富化する酸素を低減または不要とすること
が可能である。また、誘導加熱の電力投入量を調節する
ことにより、溶融スラグの温度を容易に調節することが
できる。
2) When the waste is directly melted in a shaft furnace without incineration, in the present invention, a molded product obtained by coating graphite or coke with ceramics, a molded product obtained by mixing carbon powder with ceramics, or It is possible to reduce the fuel consumption and reduce or eliminate the oxygen enriched in the air blown from the tuyere by inductively heating the conductive ceramic molded body and melting the pyrolysis residue. . Further, the temperature of the molten slag can be easily adjusted by adjusting the power input amount of the induction heating.

【0034】3)電気を使った加熱方法として、通電加
熱等の方法があるが、溶融炉の炉壁を貫通して電極を設
置する必要があり、構造が複雑となり、さらに消耗した
電極の交換が頻繁であるが、誘導加熱の場合はそのよう
な問題もない。
3) As a heating method using electricity, there is a method such as energization heating. However, it is necessary to install electrodes through the furnace wall of the melting furnace, which complicates the structure and further replaces worn-out electrodes. However, induction heating does not have such a problem.

【0035】4)コークスを炉内に装入することによ
り、従来のシャフト炉と同様に炉内を還元雰囲気にする
ことができ、溶融後のスラグ中の鉛等の重金属を揮発さ
せて低減することができるため、スラグを有効利用する
場合に、環境に対する悪影響の心配がない。従って本発
明は、スラグ中の重金属低減というシャフト炉の長所を
生かしつつ電気を使用した場合の長所を兼ね備えた廃棄
物の溶融炉である。
4) By charging coke into the furnace, the inside of the furnace can be made into a reducing atmosphere, similarly to the conventional shaft furnace, and heavy metals such as lead in the molten slag are volatilized and reduced. Therefore, when slag is used effectively, there is no concern about adverse effects on the environment. Accordingly, the present invention is a waste melting furnace having the advantages of using electricity while utilizing the advantages of a shaft furnace of reducing heavy metals in slag.

【0036】5)誘導加熱する電力としては、廃棄物の
保有する発熱量を利用して発電して有効利用することに
よって、外部から買電する必要がない。
5) As the electric power for induction heating, there is no need to purchase power from the outside by generating electricity using the calorific value of the waste and effectively utilizing it.

【0037】6)溶融処理後のスラグを再資源化するこ
とにより、スラグの処分場が不要となるだけでなく、天
然砂の採掘による自然破壊を防止することができる。
6) By recycling the slag after the melting process, not only is the slag disposal site unnecessary, but also natural destruction by mining of natural sand can be prevented.

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

【図1】 本発明一実施例を示す図である。FIG. 1 is a diagram showing one embodiment of the present invention.

【図2】 溶融炉の廃熱を利用して加熱コイルに通電で
きるようにした図である。
FIG. 2 is a diagram in which electric power can be supplied to a heating coil using waste heat of a melting furnace.

【図3】 本発明の別実施例を示す図である。FIG. 3 is a diagram showing another embodiment of the present invention.

【図4】 従来の直接溶融炉の図である。FIG. 4 is a diagram of a conventional direct melting furnace.

【符号の説明】[Explanation of symbols]

1 シャフト炉 2 廃棄物装入装置 3 上段羽
口 4 下段羽口 5 シャフト部 6 朝顔部 7 炉内下部 8
ガス排出管 9 スラグ排出口 10 加熱コイル 11 高周
波電源 12 成形体 13 成形体 14 二次燃焼室
15 ボイラー 16 排ガス冷却器 17 集塵機 18 煙突
19 コークス充填層 20 発電機
DESCRIPTION OF SYMBOLS 1 Shaft furnace 2 Waste charging device 3 Upper tuyere 4 Lower tuyere 5 Shaft part 6 Morning glory part 7 Furnace lower part 8
Gas discharge pipe 9 Slag discharge port 10 Heating coil 11 High frequency power supply 12 Molded body 13 Molded body 14 Secondary combustion chamber
15 Boiler 16 Exhaust gas cooler 17 Dust collector 18 Chimney
19 Coke packed bed 20 Generator

───────────────────────────────────────────────────── フロントページの続き (51)Int.Cl.7 識別記号 FI テーマコート゛(参考) F23G 5/46 ZAB F27B 1/00 4K045 F27B 1/00 1/16 4K056 1/16 1/20 4K063 1/20 F27D 11/06 Z F27D 11/06 17/00 101A 17/00 101 C22B 9/02 // C22B 9/02 B09B 3/00 303K (72)発明者 小佐野 秀実 北九州市戸畑区大字中原46−59 新日本製 鐵株式会社エンジニアリング事業本部内 Fターム(参考) 3K061 AA16 AB02 AB03 BA05 BA07 CA15 DA05 DA12 DA19 DB16 DB20 FA10 FA21 FA25 3K065 AA16 AB02 AB03 BA05 BA07 DA10 GA01 GA06 GA13 GA34 JA05 JA18 3K078 AA05 AA07 BA08 BA21 CA02 CA12 CA13 CA21 CA24 4D004 AA02 AA46 AB03 AC08 BA02 CA12 CA24 CA27 CA29 CA42 CB02 CB32 CB33 4K001 BA24 DA06 HA01 4K045 AA01 BA10 GB05 GB12 GC01 4K056 AA05 AA19 BA01 BB01 BB07 CA20 DA13 DA39 4K063 AA04 AA06 AA12 BA13 CA01 FA34 ──────────────────────────────────────────────────続 き Continued on the front page (51) Int.Cl. 7 Identification symbol FI Theme coat ゛ (Reference) F23G 5/46 ZAB F27B 1/00 4K045 F27B 1/00 1/16 4K056 1/16 1/20 4K061 1 / 20 F27D 11/06 Z F27D 11/06 17/00 101A 17/00 101 C22B 9/02 // C22B 9/02 B09B 3/00 303K (72) Inventor Hidemi Kosano 46-59 Nakahara, Tohara-ku, Kitakyushu New F-term in the Engineering Division of Nippon Steel Corporation (Reference) CA21 CA24 4D004 AA02 AA46 AB03 AC08 BA02 CA12 CA24 CA27 CA29 CA42 CB02 CB32 CB33 4K001 BA24 DA06 HA01 4K045 AA01 BA10 G B05 GB12 GC01 4K056 AA05 AA19 BA01 BB01 BB07 CA20 DA13 DA39 4K063 AA04 AA06 AA12 BA13 CA01 FA34

Claims (8)

【特許請求の範囲】[Claims] 【請求項1】 廃棄物をシャフト炉に装入し、炉下部の
単段または複数段の羽口から空気または酸素富化空気を
吹き込み装入された廃棄物を還元燃焼せしめ、炉上部の
シャフト部で炉内に装入された廃棄物を順次、予熱、乾
燥、熱分解させガス化した後、廃棄物の熱分解残渣を溶
融処理する方法において、炉内下部には予め黒鉛または
コークスをセラミックスで被覆した成形体、または炭素
粉をセラミックスと混合して成形した成形体、または導
電性セラミックスの成形体を配置しておき、該成形体を
誘導加熱することにより前記廃棄物の熱分解残渣を溶融
処理することを特徴とする廃棄物の溶融処理方法。
1. A waste is charged into a shaft furnace, and air or oxygen-enriched air is blown from one or a plurality of tuyeres at a lower part of the furnace to reduce and burn the charged waste. In the method of sequentially preheating, drying, pyrolyzing and gasifying the waste charged in the furnace in the section, and then melting and processing the pyrolysis residue of the waste, graphite or coke is preliminarily coated with ceramics in the lower part of the furnace. A molded body coated with, or a molded body formed by mixing carbon powder with ceramics, or a molded body of conductive ceramics is arranged, and the thermally decomposed residue of the waste is obtained by induction heating the molded body. A method for melting waste, comprising melting.
【請求項2】 請求項1記載の廃棄物の溶融処理方法に
おいて、炉内にコークスを装入して炉内を還元雰囲気と
し、重金属等の有害物質を揮発させて無害な溶融物とな
すことを特徴とする廃棄物の溶融処理方法。
2. The method for melting waste according to claim 1, wherein coke is charged into the furnace to make the furnace a reducing atmosphere, and harmful substances such as heavy metals are volatilized into a harmless melt. A method of melting and processing waste.
【請求項3】 請求項1記載の廃棄物の溶融処理方法に
おいて、ガス化したガスをシャフト炉から排出したのち
燃焼せしめ、この熱を利用して発電し、該発電した電気
を誘導加熱の電源とすることを特徴とする廃棄物の溶融
処理方法。
3. The method according to claim 1, wherein the gasified gas is discharged from a shaft furnace and then burnt, and the heat is used to generate electric power. A method for melting waste.
【請求項4】 炉頂に廃棄物の装入装置を備え、炉内部
には予熱帯、乾燥帯、熱分解帯を有し、炉体下部に単段
または複数段の羽口を備えたシャフト炉式の廃棄物溶融
炉において、炉内下部に黒鉛またはコークスをセラミッ
クスで被覆した成形体、または炭素粉をセラミックスと
混合して成形した成形体、または導電性セラミックスの
成形体を配置し、該成形体を誘導加熱するための交番電
流を通電する加熱コイルを炉下部の外周に設置したこと
を特徴とする廃棄物溶融炉。
4. A shaft having a waste charging device at the furnace top, a pre-tropical zone, a drying zone, and a pyrolysis zone inside the furnace, and a single-stage or multiple-stage tuyere below the furnace body. In a furnace-type waste melting furnace, a molded body obtained by coating graphite or coke with ceramics, a molded body formed by mixing carbon powder with ceramics, or a molded body made of conductive ceramics is disposed in the lower part of the furnace. A waste melting furnace characterized in that a heating coil for supplying an alternating current for induction heating of a formed body is provided on an outer periphery of a lower part of the furnace.
【請求項5】 請求項4記載の廃棄物溶融炉において、
炉内下部に配置する黒鉛またはコークスをセラミックス
で被覆した成形体、または炭素粉をセラミックスと混合
して成形した成形体、または導電性セラミックスの成形
体を、0.008m以下の体積の塊とし、炉内下部に
充填するようになしたことを特徴とした廃棄物溶融炉。
5. The waste melting furnace according to claim 4,
Moldings graphite or coke arranged in the lower furnace are coated with a ceramic, or moldings were formed by mixing the ceramic and carbon powder, or a molded body of a conductive ceramic, and 0.008 m 3 or less of the volume of the mass A waste melting furnace characterized in that the lower part of the furnace is filled.
【請求項6】 請求項4記載の廃棄物の溶融炉におい
て、炉内下部に配置する黒鉛またはコークスをセラミッ
クスで被覆した成形体、または炭素粉をセラミックスと
混合して成形した成形体、または導電性セラミックスの
成形体を角柱状とし、炉内下部に格子状に積み上げるよ
うになしたことを特徴とした廃棄物溶融炉。
6. The waste melting furnace according to claim 4, wherein a graphite or coke disposed at a lower part in the furnace is coated with ceramics, a molded body formed by mixing carbon powder with ceramics, or a conductive body. A waste melting furnace characterized in that the formed body of the conductive ceramics has a prismatic shape and is stacked in a lattice shape at a lower portion in the furnace.
【請求項7】 請求項4記載の廃棄物溶融炉において、
炉頂部にコークスの装入装置を設置したことを特徴とす
る廃棄物溶融炉。
7. The waste melting furnace according to claim 4,
A waste melting furnace characterized in that a coke charging device is installed at the furnace top.
【請求項8】 請求項4記載の廃棄物溶融炉において、
該溶融炉の後段に溶融炉の廃熱を利用し発電するボイラ
ーと発電機を設け、該発電機で発電した電気を溶融炉の
炉下部の外周に設置した加熱コイルに通電できるように
なしたことを特徴とする廃棄物溶融炉。
8. The waste melting furnace according to claim 4,
A boiler and a generator for generating electricity by using the waste heat of the melting furnace are provided at a stage subsequent to the melting furnace, and electricity generated by the generator can be supplied to a heating coil installed on an outer periphery of a lower portion of the melting furnace. A waste melting furnace characterized by the above-mentioned.
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JP2008508174A (en) * 2004-07-29 2008-03-21 サン−ゴバン イゾベ Method and apparatus for treating recycled textile waste
KR20110059863A (en) * 2008-08-27 2011-06-07 에스지엘 카본 에스이 Method for processing solid or molten materials
JP2018528322A (en) * 2015-06-29 2018-09-27 アーバンゴールド ゲーエムベーハー Apparatus and arrangement for metallurgical processing of electrical and / or electronic scrap or parts and their use and method for metallurgical processing of electrical and / or electronic scrap or parts
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Cited By (9)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2008508174A (en) * 2004-07-29 2008-03-21 サン−ゴバン イゾベ Method and apparatus for treating recycled textile waste
KR20110059863A (en) * 2008-08-27 2011-06-07 에스지엘 카본 에스이 Method for processing solid or molten materials
JP2012500717A (en) * 2008-08-27 2012-01-12 エスジーエル カーボン エスイー Method for processing solid or molten material
US8568507B2 (en) 2008-08-27 2013-10-29 Sgl Carbon Se Method for processing solid or molten materials
KR101643136B1 (en) 2008-08-27 2016-07-27 에스지엘 카본 에스이 Method for processing solid or molten materials
JP2018528322A (en) * 2015-06-29 2018-09-27 アーバンゴールド ゲーエムベーハー Apparatus and arrangement for metallurgical processing of electrical and / or electronic scrap or parts and their use and method for metallurgical processing of electrical and / or electronic scrap or parts
CN112272589A (en) * 2018-03-09 2021-01-26 绿色生态国际有限公司 System and method for food waste decomposition
CN115979010A (en) * 2022-12-31 2023-04-18 山东金旺装备科技有限公司 Waste heat utilization system of petroleum coke tank type calcining furnace
CN115979010B (en) * 2022-12-31 2024-03-19 山东金旺装备科技有限公司 Petroleum coke tank calciner waste heat utilization system

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