JP2001193909A - Melt processing apparatus for wastes such as incineration ash - Google Patents

Melt processing apparatus for wastes such as incineration ash

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Publication number
JP2001193909A
JP2001193909A JP37725899A JP37725899A JP2001193909A JP 2001193909 A JP2001193909 A JP 2001193909A JP 37725899 A JP37725899 A JP 37725899A JP 37725899 A JP37725899 A JP 37725899A JP 2001193909 A JP2001193909 A JP 2001193909A
Authority
JP
Japan
Prior art keywords
melting
chamber
combustion
gas
incineration ash
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Pending
Application number
JP37725899A
Other languages
Japanese (ja)
Inventor
Yasuo Kaneko
康男 兼子
Nobuo Kawakami
信雄 川上
Noriyuki Inoue
典幸 井上
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.)
Chiyoda Enji Kk
Original Assignee
Chiyoda Enji Kk
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 Chiyoda Enji Kk filed Critical Chiyoda Enji Kk
Priority to JP37725899A priority Critical patent/JP2001193909A/en
Publication of JP2001193909A publication Critical patent/JP2001193909A/en
Pending legal-status Critical Current

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  • Gasification And Melting Of Waste (AREA)
  • Processing Of Solid Wastes (AREA)

Abstract

PROBLEM TO BE SOLVED: To develop a processing apparatus capable of reducing quantity of coke consumed as much as possible, and utilizing waste plastics as a heat source up to the utmost 100% in a melt processing apparatus for incineration ash. SOLUTION: A melting furnace 11 for processing wastes W such as incineration ash and the like is provided with a gas decomposing chamber 12 forming a specified space for introducing air fed to the lower part thereof, temporarily storing slug after melting, and thermally processing. An inlet 13 for air transporting fractions of waste plastics is faced to a portion of the gas decomposing chamber 12, and a gate 16 is arranged at the upper part of the chamber 12 to accelerate rising of decomposed gas and falling of molten slug. Further, a combustion melting chamber 17 is formed with a secondary air inlet 18 for accelerating incineration with the decomposed gas and for melt processing the wastes fed into the combustion melting chamber 17.

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、焼却灰等の廃棄物
を溶融処理する為の装置に関し、更に詳細には、廃棄プ
ラスチックを熱源に活用した処理装置に関する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to an apparatus for melting waste such as incineration ash, and more particularly to an apparatus utilizing waste plastic as a heat source.

【0002】[0002]

【従来の技術】焼却灰の成分は、大略CaO15〜16
%、SiO35〜36%、Al17〜18%、
その他3%程度から成るもので、1300〜1800℃
の温度下で溶融し、従来、該焼却灰は、コークス充填式
のシャフト炉内で、コークスと焼却灰の塊とを交互に層
状に重ね合わせ、該コークスの燃焼熱で1300〜18
00℃に導いて溶融スラグとし、冷却後、破砕処理され
ている。
2. Description of the Related Art The components of incinerated ash are generally CaO 15-16.
%, SiO 2 35~36%, Al 2 O 3 17~18%,
Others consisting of about 3%, 1300-1800 ° C
Conventionally, the incinerated ash is obtained by laminating coke and incinerated ash in layers alternately in a coke-filled shaft furnace.
The molten slag is led to 00 ° C., cooled, and crushed.

【0003】そして、該コークス充填式シャフト炉によ
る処理は、炉の構造が簡潔であると共に炉内の高温が得
やすいことから、焼却灰の処理に適した方法との評価を
得ているが、しかし、該シャフト炉にあっても、焼却灰
の3〜4割のコークスを必要とし、該コークスが高価で
あることから、エネルギーコストが高いという欠点を残
している。
[0003] The treatment with the coke-filled shaft furnace has been evaluated as a method suitable for treating incineration ash because the furnace structure is simple and a high temperature in the furnace is easily obtained. However, even in the case of the shaft furnace, 30 to 40% of coke of incinerated ash is required, and since the coke is expensive, there is a disadvantage that energy cost is high.

【0004】そこで、従来、これを改良せんとして、低
コストのガス又は油及び固体燃料を導入口より吹き込ん
で、コークスによる燃焼の補助的手段としようとする方
法が一部で試みられており、そして、この固体燃料に、
廃棄プラスチックを用いる手段も検討されている。しか
し、該廃棄プラスチックをそのまま炉内に投入すると、
それが溶融する段階で塊状となり、細孔を備えたコーク
スの目詰まりを起こすこととなるので、その燃焼量には
限界があり、コークス燃焼量の10%以下に過ぎないも
のであった。
In view of the above, in order to improve the above, some methods have been attempted in which low-cost gas or oil and solid fuel are blown from an inlet so as to be used as auxiliary means for combustion by coke. And this solid fuel,
Means of using waste plastics are also being considered. However, when the waste plastic is put into the furnace as it is,
At the stage of melting, the coke becomes blocky and causes clogging of the coke having pores. Therefore, the amount of combustion is limited and is only 10% or less of the amount of coke burned.

【0005】[0005]

【発明が解決しようとする課題】本発明は上記実情を解
消しようとしてなされたもので、コークスの使用量を可
及的に最少のものとし、廃棄プラスチックを熱源として
最大100%にまで利用可能な処理装置を開発しようと
するものである。
DISCLOSURE OF THE INVENTION The present invention has been made in order to solve the above-mentioned situation, and it is possible to minimize the amount of coke used and to use up to 100% of waste plastic as a heat source. It is intended to develop a processing device.

【0006】[0006]

【課題を解決するための手段】本発明溶融処理装置は、
焼却灰等の廃棄物を溶融処理する溶融炉において、該溶
融炉の下部に搬送空気を導入すると共に溶融後のスラグ
を一時的に滞留させて廃棄プラスチックを熱分解する為
の一定空間を形成したガス分解室を配設し、該ガス分解
室の一部に廃棄プラスチックの細片を搬入する搬送空気
の導入口を臨ませ、該ガス分解室の上部に分解ガスの上
昇と溶融スラグの滴下を促すロストルを配すると共に分
解ガスとの燃焼を促す空気導入口を臨ませた燃焼溶融室
を形成し、該燃焼溶融室に廃棄物を投入して溶融処理す
ることを特徴として構成される。
SUMMARY OF THE INVENTION The melt processing apparatus of the present invention comprises:
In a melting furnace for melting and processing waste such as incineration ash, a certain space for thermally decomposing waste plastic was formed by introducing carrier air into the lower part of the melting furnace and temporarily retaining slag after melting. A gas cracking chamber is provided, and a part of the gas cracking chamber faces the inlet of the carrier air for carrying the waste plastic pieces, and the rising of the cracked gas and the dripping of the molten slag are performed at the top of the gas cracking chamber. A combustion melting chamber is formed facing the air inlet for arranging a roster to promote the combustion with the decomposition gas, and a waste is put into the combustion melting chamber to perform a melting process.

【0007】[0007]

【発明の実施の形態】本発明溶融処理装置は、焼却灰等
の廃棄物Sを溶融させる溶融炉部10と、これに廃棄プ
ラスチックを供給する廃棄プラスチック導入部30とか
ら成る。
DETAILED DESCRIPTION OF THE PREFERRED EMBODIMENTS The melting apparatus according to the present invention comprises a melting furnace section 10 for melting waste S such as incineration ash and a waste plastic introducing section 30 for supplying waste plastic thereto.

【0008】該溶融炉部の溶融炉11には、シャフト型
溶融炉を用いることができ、該溶融炉の下部に後述の搬
送空気を迎え入れると共に溶融後のスラグGを一時的に
滞留させる為の一定空間を形成したガス分解室12を配
設する。該ガス分解室12の一部には、該搬送空気の導
入口13を配設し、他方には後述する初期の予備加熱を
司るバーナー14を配設し、下部に排出口15を配設す
る。尚、導入口13には、後述の二次空気の導入と同
様、熱交換機を経由した比較的高温の空気の導入管を併
用させても良く、又、必要に応じて該空気に酸素富化器
19を付設させても良い。
As the melting furnace 11 of the melting furnace, a shaft type melting furnace can be used. The lower part of the melting furnace is used for receiving the below-mentioned carrier air and for temporarily retaining the slag G after melting. A gas decomposition chamber 12 forming a certain space is provided. A part of the gas decomposition chamber 12 is provided with an inlet 13 for the carrier air, the other side is provided with a burner 14 for performing initial preheating described later, and a lower part is provided with an outlet 15. . The inlet 13 may be used together with a relatively high-temperature air inlet pipe via a heat exchanger, as in the case of the secondary air described below. If necessary, the air may be enriched with oxygen. A vessel 19 may be provided.

【0009】該ガス分解室12の上には、分解ガスの上
昇と溶融スラグの滴下を促すロストル16を配し、その
上には予備加熱の為の耐火物片ベッドを配し、更にその
上に塊状の焼却灰Sを充填すべき燃焼溶融室17を形成
する。該燃焼溶融室17には、一部に高温燃焼を促す為
の二次空気導入口18を臨ませ、該二次空気導入口18
には、燃焼ガスとの熱交換機を経由した比較的高温の空
気を導入管から送気する。
On the gas decomposition chamber 12, there is arranged a rostre 16 for promoting the rise of the decomposition gas and dripping of the molten slag, on which a refractory piece bed for preheating is arranged. A combustion melting chamber 17 to be filled with massive incineration ash S is formed. The combustion / melting chamber 17 partially faces a secondary air inlet 18 for promoting high-temperature combustion.
, Relatively high-temperature air that has passed through a heat exchanger with the combustion gas is supplied from an inlet pipe.

【0010】更に、溶融炉11の燃焼溶融室17の上に
は、燃焼前の塊状焼却灰を予熱させる為の予備加熱室2
0を形成し、その上の炉頭部には焼却灰の投入口21及
び燃焼後の排ガスを送り出す排気口22を形成する。
Further, a preheating chamber 2 for preheating massive incineration ash before combustion is provided above the combustion melting chamber 17 of the melting furnace 11.
0 is formed, and an inlet 21 for incineration ash and an exhaust port 22 for sending out exhaust gas after combustion are formed in the furnace head above it.

【0011】そして、上記ガス分解室12の一部に臨む
搬送空気の導入口13には、搬送空気パイプ31を連結
し、且つ、その管路の一部に適当形状の細片に切断した
廃棄プラスチックを蓄えて搬送空気中に送り出すホッパ
ー32及び定量供給機33を配設する。該搬送空気パイ
プ31の先には、ブロワー34を配設し、該ブロワーは
炉内の圧力が高い場合には、高圧の加わる形態とする。
又、上記プラスチック細片には、粒状のものも含まれ
る。
A conveying air pipe 31 is connected to the conveying air inlet 13 facing a part of the gas decomposition chamber 12, and a part of the pipe is cut into small pieces of an appropriate shape. A hopper 32 and a fixed-rate feeder 33 for storing plastic and sending it into the carrier air are provided. A blower 34 is provided at the end of the conveying air pipe 31. When the pressure in the furnace is high, the blower is configured to apply high pressure.
In addition, the above-mentioned plastic strips include granular ones.

【0012】尚、本発明の熱源としての廃棄プラスチッ
クの対象物には、燃焼によってダイオキシン等の有毒ガ
スを発生する塩素系プラスチック等は除外するが、それ
以外の適当大きさに裁断又は成形可能なもの、例えばタ
イヤ等全てのプラスチックを含む。又、該廃棄プラスチ
ックの中には、溶融温度を大幅に落とさない範囲で、も
み殻、木くず、古紙等を混焼させても良い。
The object of waste plastic as a heat source of the present invention excludes chlorine-based plastics and the like, which generate toxic gas such as dioxin by combustion, but can be cut or molded into other suitable sizes. Including all plastics such as tires. In addition, rice husks, wood chips, waste paper, and the like may be mixed in the waste plastic as long as the melting temperature is not significantly reduced.

【0013】次に、本発明装置の作用を説明する。先
ず、溶融炉11内に、焼却灰を豆タン状に塊状化させた
もの、又は、該焼却灰をセメントと混練させて塊状化さ
せたものを、投入口21から投入機等を用いて投下す
る。但し、該焼却灰は、塊状化させたものばかりでな
く、紛状のまま投入しても良い。
Next, the operation of the device of the present invention will be described. First, incinerator ash obtained by agglomerating the incinerated ash into a bean tongue or kneading the incinerated ash with cement into an agglomerate is dropped into the melting furnace 11 from the input port 21 using a charging machine or the like. I do. However, the incinerated ash is not limited to agglomerated one, and may be supplied as a powder.

【0014】そして、予備加熱に移り、バーナー14に
点火して、炉内の温度を上昇させ、耐火物片ベッド等に
蓄熱させて、炉内を1500〜1800℃程度の高温に
導く。すると、上述の如く、CaO、SiO、Al
等を主成分とする焼却灰は溶融点に達し、その溶融
スラグの一部がロストル16を経て、ガス分解室12の
底部に滴下される。
Then, the process proceeds to preheating, ignites the burner 14, raises the temperature inside the furnace, stores heat in a refractory piece bed or the like, and guides the inside of the furnace to a high temperature of about 1500 to 1800 ° C. Then, as described above, CaO, SiO 2 , Al 2
The incinerated ash mainly composed of O 3 or the like reaches the melting point, and a part of the molten slag is dropped to the bottom of the gas decomposition chamber 12 through the rostre 16.

【0015】その時点で、バーナー14の燃焼を停止さ
せる。そして一方、空気を送る為のブロワー34の運転
を開始し、その途中でホッパー32から適当形状の細片
に裁断した廃棄プラスチックを搬送空気中に定量供給機
33を経て送り出し、この廃棄プラスチックを搬送空気
と共に導入口13を経てガス分解室12内に送り込む。
At that time, the combustion of the burner 14 is stopped. On the other hand, the operation of the blower 34 for sending air is started, and on the way, the waste plastic cut into small pieces of an appropriate shape is sent out from the hopper 32 into the transport air through the quantitative feeder 33, and the waste plastic is transported. It is sent into the gas decomposition chamber 12 through the inlet 13 together with air.

【0016】すると、該ガス分解室12内は、上記溶融
スラグがその底部に滞留しているので、室内が1500
〜1800℃の高温に保たれた状態となり、そしてそこ
に搬送空気によって廃棄プラスチックの細片が運び込ま
れると、該プラッスチック細片は、一部が燃焼するもの
のその殆どは熱分解して可燃ガスに変成する。即ち、ガ
ス分解室内は滞留する溶融スラグからの熱放射、対流等
の熱エネルギーの供給を受けて、室内が常に溶融温度と
ほぼ等しい温度に保たれることとなり、かかる高温下で
は、ポリエチレン、ポリスチレン等の廃棄プラスチック
は、分子間結合が解かれて一気に熱分解し、可燃ガスに
変化する。尚、前述した通り、斯かる高温下では、導入
された搬送空気と可燃物としてのプラスチックが存在す
れば当然に燃焼するが、それは一部であり、且つ、その
燃焼は後述するスラグの溶融を妨げない。
Then, in the gas decomposition chamber 12, since the molten slag stays at the bottom of the gas decomposition chamber 12, 1500
When it is kept at a high temperature of 11800 ° C., and the waste plastic particles are carried by the carrier air, the plastic flakes are partially burned, but most of them are thermally decomposed into flammable gas. Metamorphose. That is, the gas decomposition chamber receives heat radiation from the molten slag staying therein, heat energy such as convection and the like, and the chamber is always kept at a temperature substantially equal to the melting temperature. Waste plastics such as are broken down at a stretch by intermolecular bonds and are thermally decomposed to change to combustible gas. As described above, under such a high temperature, if the introduced carrier air and the plastic as a combustible are present, they naturally burn, but part of the combustion and the burning of slag which will be described later. Do not hinder.

【0017】ここで、搬入される廃棄プラスチックの大
きさ及び形状は、瞬時に熱分解可能なもので、且つ、空
気による搬送が可能なものでなけらばならず、この為に
は、可級的に小さな細片が望ましいが、本発明者の実験
では、直径20mm以下の細片であれば問題がないこと
が確認された。
Here, the size and shape of the waste plastic to be carried in must be such that it can be pyrolyzed instantaneously and that it can be transported by air. Although small strips are desirable, it has been confirmed by the inventor's experiments that there is no problem with strips having a diameter of 20 mm or less.

【0018】次いで該可燃ガスは、ロストル16の孔を
通して、燃焼溶融室17内に上昇し、そこで二次空気導
入口18から導かれた空気と反応して燃焼を起こす。こ
のとき、該廃棄プラスチックの分解した可燃ガスの熱カ
ロリーの値は、コークスが7000〜8000kcal
/kgであるのに対し、約8000〜9000kcal
/kgの値を示し、極めてカロリー値が高く、且つ、そ
の熱交換機を通した二次空気は、比較的高温に保たれて
いる。従って、そこから発生する燃焼熱は、従来のコー
クスと同等又はそれ以上であって、その結果、塊状の焼
却灰は円滑に溶融点に至り、溶融スラグGとなる。
Next, the combustible gas rises into the combustion and melting chamber 17 through the hole of the roastle 16, where it reacts with the air introduced from the secondary air inlet 18 to cause combustion. At this time, the value of the thermal calorie of the decomposed combustible gas of the waste plastic is 7000 kcal to 8000 kcal.
/ Kg, about 8000-9000 kcal
/ Kg, a very high calorie value, and the secondary air passed through the heat exchanger is kept at a relatively high temperature. Therefore, the combustion heat generated therefrom is equal to or higher than that of the conventional coke, and as a result, the massive incinerated ash smoothly reaches the melting point and becomes molten slag G.

【0019】このとき、廃棄プラスチックは、瞬時にガ
ス化して焼却灰等と接触するので、塊状の焼却灰をくま
なく囲繞し、且つ、目詰まり等を起こす恐れがなく、溶
融に適した燃焼形態となる。
At this time, the waste plastic is instantaneously gasified and comes into contact with the incineration ash and the like, so that the waste plastic surrounds the lump incineration ash without any risk of clogging or the like, and has a combustion form suitable for melting. Becomes

【0020】斯かる手段による廃棄プラスチックの燃焼
は、コークスの存在を殆ど必要とせず、コークスを10
0%置き換えた場合でも、本発明者らの実験は成功して
いる。但し、熱源としてコークスを併用することも否定
するものではない。
The combustion of waste plastics by such means requires little coke and requires less than 10 coke.
Even with 0% replacement, our experiments were successful. However, use of coke as a heat source is not denied.

【0021】そして、該溶融スラグGは、ロストル16
の孔を通して滴下し、ガス分解室12の底部に蓄えら
れ、前述のガス分解室を高温に保つ溶融スラグとしての
働きを成した後、排出口15から流下して、本来の粉砕
処理等に移される。この工程が順次繰り返される。
[0021] The molten slag G is
And is stored at the bottom of the gas decomposition chamber 12 and acts as a molten slag for keeping the gas decomposition chamber at a high temperature. Then, it flows down from the discharge port 15 and is transferred to the original pulverizing process or the like. It is. This step is sequentially repeated.

【0022】尚、上記処理の対象物として焼却灰を例に
説明したが、同様の原理で処理が可能な廃棄物であれば
これに限定されるものではなく、製鉄スラッジ、ガラス
屑、金属スラッジ、金属屑その他にも広く応用が可能で
ある。
Although incineration ash has been described as an example of the object of the above-mentioned treatment, the invention is not limited to such waste as long as it can be treated according to the same principle. It can be widely applied to metal scraps and others.

【0023】[0023]

【発明の効果】以上の構成及び作用に基づいて本発明
は、以下の如き効果を奏する。 (1)熱源として殆どコークスを使用することなく全て
を廃棄プラスチックに置き換えることができるので、エ
ネルギーコストを大幅に削減することができ、且つ、廃
棄物として処理に困窮しているプラスチックを利用する
ので、資源活用の上からも望ましい。
The present invention has the following effects based on the above configuration and operation. (1) Since almost all of the waste plastic can be replaced with waste plastic without using coke as a heat source, energy costs can be greatly reduced, and plastic which is in need of disposal as waste is used. It is also desirable from the viewpoint of resource utilization.

【0024】(2)廃棄プラスチックをそのまま燃焼さ
せるのでなく、一旦、高温下で熱分解させて可燃ガスと
し、且つ、それを処理対象物を囲繞しつつ二次空気との
混合で燃焼させるので、接触効率が良好で且つ目詰り等
の問題を惹起することがない等、溶融に最適な加熱形態
となる。
(2) Instead of burning the waste plastic as it is, it is once thermally decomposed at a high temperature to produce a combustible gas, which is burned by mixing with the secondary air while surrounding the object to be treated. The heating mode is optimal for melting, for example, it has good contact efficiency and does not cause problems such as clogging.

【0025】(3)更に、その廃棄プラスチックの熱分
解にあって、当初だけバーナーの燃焼を必要とするが、
それ以降は副成物としての溶融スラグの熱エネルギーを
利用するので、前記エネルギーコストの削減を更に進め
る。
(3) Further, in the thermal decomposition of the waste plastic, burning of the burner is required only at the beginning.
Thereafter, since the thermal energy of the molten slag as a by-product is used, the energy cost is further reduced.

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

【図1】 本発明装置の断面図。FIG. 1 is a cross-sectional view of the device of the present invention.

【符号の説明】[Explanation of symbols]

10 溶融炉部 11 溶融炉 12 ガス分解室 13 搬送空気導入口 14 バーナー 15 排出口 16 ロストル 17 燃焼溶融室 18 二次空気導入口 19 酸素富化器 20 予備加熱室 21 投入口 22 排気口 30 廃棄プラスチック導入部 31 搬送空気パイプ 32 ホッパー 33 定量供給機 34 ブロワー DESCRIPTION OF SYMBOLS 10 Melting furnace part 11 Melting furnace 12 Gas decomposition chamber 13 Conveying air introduction port 14 Burner 15 Outlet 16 Rostor 17 Combustion melting chamber 18 Secondary air introduction port 19 Oxygen enricher 20 Preheating chamber 21 Input port 22 Exhaust port 30 Disposal Plastic introduction unit 31 Conveying air pipe 32 Hopper 33 Fixed-quantity feeder 34 Blower

───────────────────────────────────────────────────── フロントページの続き (72)発明者 井上 典幸 栃木県小山市城東6−6−4 株式会社千 代田エンジ内 Fターム(参考) 3K061 AA16 AB03 AC03 AC13 CA01 CA08 4D004 AA07 AA36 CA29 CB01 CB05 CB34 CB36 CB42 CC17 DA02 DA06  ──────────────────────────────────────────────────続 き Continued on the front page (72) Inventor Noriyuki Inoue 6-6-4 Joto, Oyama-shi, Tochigi F-term in Chiyoda Engi Co., Ltd. (Reference) 3K061 AA16 AB03 AC03 AC13 CA01 CA08 4D004 AA07 AA36 CA29 CB01 CB05 CB34 CB36 CB42 CC17 DA02 DA06

Claims (3)

【特許請求の範囲】[Claims] 【請求項1】 焼却灰等の廃棄物を溶融処理する溶融炉
において、 該溶融炉の下部に搬送空気を導入すると共に溶融後のス
ラグを一時的に滞留させて廃棄プラスチックを熱分解す
る為の一定空間を形成したガス分解室を配設し、 該ガス分解室の一部に廃棄プラスチックの細片を搬入す
る搬送空気の導入口を臨ませ、 該ガス分解室の上部に分解ガスの上昇と溶融スラグの滴
下を促すロストルを配すると共に分解ガスとの燃焼を促
す空気導入口を臨ませた燃焼溶融室を形成し、該燃焼溶
融室に廃棄物を投入して溶融処理することを特徴とする
溶融処理装置。
1. A melting furnace for melting waste such as incineration ash, wherein a conveying air is introduced into a lower part of the melting furnace and a slag after melting is temporarily retained to thermally decompose waste plastic. A gas decomposition chamber having a certain space is provided, and a part of the gas decomposition chamber faces an inlet of a carrier air for carrying a small piece of waste plastic. Forming a combustion melting chamber facing the air inlet for promoting the combustion with the decomposition gas while arranging a rostelle for promoting the dropping of the molten slag, and introducing and melting the waste into the combustion and melting chamber. Melt processing equipment.
【請求項2】 ガス分解室の一部に予備加熱の為のバー
ナーを配設した請求項1記載の溶融処理装置。
2. The melt processing apparatus according to claim 1, wherein a burner for preheating is provided in a part of the gas decomposition chamber.
【請求項3】 燃焼溶融室の一部に、予備加熱の為の耐
火物片ベッドを配設した請求項1,2いずれか1項記載
の溶融処理装置。
3. The melting treatment apparatus according to claim 1, wherein a refractory piece bed for preheating is provided in a part of the combustion melting chamber.
JP37725899A 1999-12-29 1999-12-29 Melt processing apparatus for wastes such as incineration ash Pending JP2001193909A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP37725899A JP2001193909A (en) 1999-12-29 1999-12-29 Melt processing apparatus for wastes such as incineration ash

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP37725899A JP2001193909A (en) 1999-12-29 1999-12-29 Melt processing apparatus for wastes such as incineration ash

Publications (1)

Publication Number Publication Date
JP2001193909A true JP2001193909A (en) 2001-07-17

Family

ID=18508522

Family Applications (1)

Application Number Title Priority Date Filing Date
JP37725899A Pending JP2001193909A (en) 1999-12-29 1999-12-29 Melt processing apparatus for wastes such as incineration ash

Country Status (1)

Country Link
JP (1) JP2001193909A (en)

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