JP2001193920A - Device for fusing incinerated ash, coupled with rotary kiln incinerator - Google Patents

Device for fusing incinerated ash, coupled with rotary kiln incinerator

Info

Publication number
JP2001193920A
JP2001193920A JP37726099A JP37726099A JP2001193920A JP 2001193920 A JP2001193920 A JP 2001193920A JP 37726099 A JP37726099 A JP 37726099A JP 37726099 A JP37726099 A JP 37726099A JP 2001193920 A JP2001193920 A JP 2001193920A
Authority
JP
Japan
Prior art keywords
combustion
chamber
gas
melting
furnace
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
JP37726099A
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 JP37726099A priority Critical patent/JP2001193920A/en
Publication of JP2001193920A publication Critical patent/JP2001193920A/en
Pending legal-status Critical Current

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

Abstract

PROBLEM TO BE SOLVED: To develop a device which minimizes the quantity of used coke as far as possible when performing the fusion treatment of incinerated ash discharged from an incinerator and can utilize scrapped plastic to 100% at maximum as a heat source in the rotary kiln type of incinerator. SOLUTION: For this fusion disposer, a fusion furnace 20 is coupled with a discharge port for incinerated ash produced from a rotary kiln type of furnace 10. Fusion furnace 20 is constituted in such a way as (a) to arrange a gas cracking chamber 22, where a certain space for thermally cracking scrapped plastic by introducing carrying air and staying slag fusion temporarily is made at its lower part; (b) to let an introduction port 23 for carrying air for carrying in the pieces of scrapped plastic front on one pat of that gas cracking chamber; and (c) to form a combustion fusion chamber 27, where a luster 26 for accelerating the rise of cracked gas and the drop of fused slug is arranged above in that gas cracking chamber, and also an air introduction port for accelerating the combustion with cracked gas fronts on it, at its upper part of that gas cracking chamber, and to lead incinerated ash into that combustion fusion chamber so as to fuse it.

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、ロータリーキルン
式焼却炉に連結した焼却灰を溶融処理する為の装置に関
し、更に詳細には、該溶融に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 and processing incinerated ash connected to a rotary kiln incinerator, and more particularly to a processing apparatus utilizing waste plastic as a heat source for the melting.

【0002】[0002]

【従来の技術】油泥、タール、ピッチ、塗料等の粘稠
物、染料かす等の粉・粒状物等のゴミを処分する有効な
手段として、ロータリーキルン式焼却炉が従来用いられ
ている。そのロータリーキルン式焼却炉の概要は、例え
ば後燃焼ストーカ付のものでは、円筒形のキルン本体
と、該キルンを回転させる駆動部と、キルン内の燃焼室
に廃棄物を供給する供給部と、該燃焼室に燃焼空気を供
給する空気供給部とから成っている。 これに後燃焼ス
トーカを連設し、その上に二次燃焼室を設け、下方に生
成された焼却灰を排出する排出コンベアを配設して成
る。そして、その焼却灰の成分は、大略CaO 15〜
16%、SiO35〜36%、Al17〜18
%、その他3%程度から成るもので、1300〜180
0℃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〜
1800℃に導いて溶融スラグとし、冷却後、破砕処理
されているのが一般的である。
2. Description of the Related Art Rotary kiln incinerators have been used as an effective means for disposing of viscous substances such as oil mud, tar, pitch, and paint, and powder and granular substances such as dye residue. The outline of the rotary kiln-type incinerator is, for example, in a case with a post-combustion stoker, a cylindrical kiln body, a driving unit for rotating the kiln, a supply unit for supplying waste to a combustion chamber in the kiln, And an air supply unit for supplying combustion air to the combustion chamber. A post-combustion stoker is connected to this, a secondary combustion chamber is provided thereon, and a discharge conveyor for discharging generated incineration ash is provided below. The components of the incinerated ash are generally CaO 15 ~
16%, SiO 2 35~36%, Al 2 O 3 17~18
%, And about 3%, from 1300 to 180
Melting at a temperature of 0 ° C., conventionally, the incinerated ash is formed by laminating layers of coke and incinerated ash alternately in a coke-filled shaft furnace, and the heat of combustion of the coke is 1300 to 1300.
It is general that the molten slag is led to 1800 ° C., cooled, and crushed.

【0003】しかし、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
得ているものの、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] However, the treatment using 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. 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、油泥、タール、ピッ
チ、塗料等の粘稠物、染料かす等の粉・粒状物等のゴミ
を処分するロータリーキルン式焼却炉にあって、焼却炉
と溶融処理装置とを連結させ、且つ、焼却炉から排出さ
れる焼却灰の溶融処理を行うに際し、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 circumstances, and disposes viscous materials such as oil mud, tar, pitch and paint, and dusts and dusts such as dye residues. In a rotary kiln-type incinerator, the incinerator and the melting treatment device are connected, and the amount of coke used is minimized when melting the incineration ash discharged from the incinerator, The aim is to develop a device that can utilize up to 100% of waste plastic as a heat source.

【0006】[0006]

【課題を解決するための手段】本発明溶融処理装置は、
円筒形のキルンを軸心回りに回転させ、その内部に燃焼
空気を送り込んで燃焼室を形成して成るロータリーキル
ン式焼却炉から生成される焼却灰の排出口に連結させて
溶融炉を形成し、該溶融炉を、(a)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、(b)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、(c)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、該燃焼溶融室に焼却灰を導いて溶融処理するように
して構成される。
SUMMARY OF THE INVENTION The melt processing apparatus of the present invention comprises:
A cylindrical kiln is rotated around its axis, and combustion air is fed into the cylindrical kiln and connected to an outlet of incinerated ash generated from a rotary kiln incinerator formed by forming a combustion chamber, thereby forming a melting furnace. In the melting furnace, (a) a gas decomposition chamber is provided at a lower portion, in which a carrier air is introduced and a fixed space for thermally decomposing waste plastic by temporarily retaining the slag after melting is provided; A) A part of the gas decomposition chamber facing the inlet of the carrier air for carrying the waste plastic strips, and (c) a locator is provided at the upper part of the gas decomposition chamber to promote the rise of the decomposition gas and the dripping of the molten slag. At the same time, a combustion melting chamber is formed facing the air inlet for promoting combustion with the decomposition gas, and the incineration ash is guided to the combustion melting chamber for melting.

【0007】[0007]

【発明の実施の形態】本発明溶融処理装置は、ロータリ
ーキルン式焼却炉部10と、そこから生成される焼却灰
Sを溶融させる溶融炉部20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40とから成る。
DETAILED DESCRIPTION OF THE PREFERRED EMBODIMENTS A melting treatment apparatus according to the present invention comprises a rotary kiln type incinerator unit 10, a melting furnace unit 20 for melting incineration ash S generated therefrom, and a waste plastic introduction unit for supplying waste plastic to the unit. 40.

【0008】該ロータリーキルン式焼却炉は、円筒形の
キルンを軸心回りに回転させ、その内部に燃焼空気を送
り込んで燃焼室を形成して燃焼処理を行う焼却炉全体を
指す。炉外には、ゴミの貯留槽11と、そこから一定量
を炉内に供給する定量供給装置12を備える。円筒形の
キルン本体13を形成し、その一部にこれを軸心回りに
回転させる駆動部14を連結し、側面に燃焼空気の導入
口15を配設し、その下に始動用バーナ16を配設す
る。そして、該炉の終端部に焼却後の灰を排出する為の
排出口17を形成する。
The rotary kiln-type incinerator refers to an entire incinerator that rotates a cylindrical kiln around an axis, feeds combustion air into the inside, forms a combustion chamber, and performs a combustion process. Outside the furnace, there is provided a storage tank 11 for garbage, and a fixed amount supply device 12 for supplying a fixed amount of the waste into the furnace. A cylindrical kiln body 13 is formed, a driving part 14 for rotating the kiln body 13 around an axis is connected to a part thereof, a combustion air inlet 15 is provided on a side surface, and a starter burner 16 is provided below the inlet 15. Arrange. Then, a discharge port 17 for discharging the incinerated ash is formed at the end of the furnace.

【0009】次いで、該ロータリーキルン式焼却炉部1
0の排出口17に連結させて、溶融炉部20を形成す
る。該排出口17と溶融炉部20との連結の形態は、図
1の如く、排出口17の直下に溶融炉部20を配置させ
るもの、又は、図示しないが、一旦排出口から落下した
焼却灰をコンベア等で投入口31から投下するもの等と
することができ、いずれも焼却灰を粘結剤等で塊状化す
る等の処理を施すことなく、粉状の焼却灰のまま溶融炉
部20に投入する形態のものとする。
Next, the rotary kiln incinerator unit 1
The melting furnace section 20 is formed by being connected to the discharge port 17 of the melting furnace. The form of connection between the discharge port 17 and the melting furnace section 20 is such that the melting furnace section 20 is disposed immediately below the discharge port 17 as shown in FIG. 1 or, although not shown, incineration ash once dropped from the discharge port Can be dropped from the input port 31 by a conveyor or the like. In any case, the powdered incinerated ash is kept in the melting furnace section 20 without any treatment such as agglomerating the incinerated ash with a binder or the like. Into the form.

【0010】該溶融炉部20の溶融炉21には、図2に
示す如く、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22を配設する。該ガス分解室22の一部
には、該搬送空気の導入口23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24を配設し、下部
に排出口25を配設する。尚、導入口23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29を付設させても良い。
As shown in FIG. 2, a shaft-type melting furnace can be used as the melting furnace 21 of the melting furnace section 20, and a slag G after melting is introduced into the lower part of the melting furnace while conveying air to be described later. A gas decomposition chamber 22 having a certain space for temporarily staying is provided. A part of the gas decomposition chamber 22 is provided with an inlet 23 for the carrier air, the other side is provided with a burner 24 for performing initial preliminary heating described later, and a lower part is provided with an outlet 25. . In addition, as with the introduction of the secondary air described later, a relatively high-temperature air introduction pipe via a heat exchanger may be used together with the introduction port 23. If necessary, the air may be enriched with oxygen. A vessel 29 may be provided.

【0011】該ガス分解室22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26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
上に焼却灰Sを充填すべき燃焼溶融室27を形成する。
該燃焼溶融室27には、一部に高温燃焼を促す為の二次
空気導入口28を臨ませ、該二次空気導入口28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 top of the gas decomposition chamber 22, there is arranged a roster 26 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 27 to be filled with incineration ash S is formed.
A secondary air inlet 28 for promoting high-temperature combustion is partially exposed to the combustion / melting chamber 27. The secondary air inlet 28
Relatively high-temperature air that has passed through a heat exchanger with the combustion gas is sent from the inlet pipe.

【0012】更に、溶融炉21の燃焼溶融室27の上に
は、溶融前の焼却灰を予熱させる為の予備加熱室30を
形成し、その上の炉頭部にキルン式焼却炉の排出口17
を連結させる。
Further, a preheating chamber 30 for preheating the incineration ash before melting is formed above the combustion melting chamber 27 of the melting furnace 21, and a discharge port of the kiln incinerator is provided at the furnace head above the preheating chamber 30. 17
Are linked.

【0013】そして、上記ガス分解室22の一部に臨む
搬送空気の導入口23には、搬送空気パイプ41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42及び定量供給機43を配設する。該搬送空気パイ
プ41の先には、ブロワー44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 transport air pipe 41 is connected to the transport air inlet 23 facing a part of the gas decomposition chamber 22, and a part of the conduit is cut into small pieces of an appropriate shape. A hopper 42 and a metering device 43 for storing the plastic and sending it into the carrier air are provided. A blower 44 is provided at the end of the conveying air pipe 41. 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.

【0014】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 the waste plastic as the heat source of the present invention excludes chlorinated 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.

【0015】次に、本発明装置の作用を説明する。先
ず、ロータリーキルン式燃焼炉部10では、貯留させた
ゴミを定量供給装置12を経て、キルン本体13内に導
くと、始動バーナ16の火炎と燃焼空気導入口15から
の空気でゴミが燃焼する。このとき円筒形のキルン本体
13が駆動部14によって軸心回りに回転するので、燃
焼の輻射熱及び高速壁面伝達加熱によりゴミ全体がまん
べんなく燃焼する。斯くして、キルンによる燃焼を経て
焼却灰が生成され、それが排出口17を経て排出され
る。
Next, the operation of the device of the present invention will be described. First, in the rotary kiln type combustion furnace section 10, when the stored dust is guided into the kiln body 13 via the quantitative supply device 12, the dust is burned by the flame of the starting burner 16 and the air from the combustion air inlet 15. At this time, since the cylindrical kiln body 13 is rotated around the axis by the driving unit 14, the entire dust is uniformly burned by the radiant heat of the combustion and the high-speed wall transfer heating. In this way, incineration ash is generated through the combustion by the kiln and is discharged through the outlet 17.

【0016】すると、該排出口17の下に配された溶融
炉部20の投入口31から、粉状の焼却灰Sがそのまま
炉内に投入される。又は、図示しないが、コンベア等を
用いた場合には、そのコンベアから粉状の焼却灰が投下
される。
Then, the powdered incineration ash S is directly charged into the furnace from the charging port 31 of the melting furnace section 20 disposed below the discharge port 17. Alternatively, although not shown, when a conveyor or the like is used, powdery incineration ash is dropped from the conveyor.

【0017】次に、予備加熱に移り、バーナー24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26を経て、ガス分解室22の底
部に滴下される。
Next, the process proceeds to preheating, in which the burner 24 is ignited to raise the temperature in the furnace, to store heat in a refractory piece bed or the like, and to guide the inside of the furnace to a high temperature of about 1500 to 1800 ° C. Then, as described above, CaO, SiO 2 , Al 2 O
The incinerated ash mainly composed of 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 22 through the rostre 26.

【0018】その時点で、バーナー24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44の運転
を開始し、その途中でホッパー42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
43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23を経てガス分解室22内に送り込む。
At that time, the combustion of the burner 24 is stopped. On the other hand, the operation of the blower 44 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 42 into the transport air via the quantitative feeder 43, and the waste plastic is transported. It is sent into the gas decomposition chamber 22 through the inlet 23 together with air.

【0019】すると、該ガス分解室22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 22, since the molten slag stays at the bottom of the gas decomposition chamber 22, 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.

【0020】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 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.

【0021】次いで該可燃ガスは、ロストル26の孔を
通して、燃焼溶融室27内に上昇し、そこで二次空気導
入口28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、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 27 through the hole of the roastle 26, where it reacts with the air introduced from the secondary air inlet 28 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 incinerated ash reaches the melting point smoothly and becomes molten slag G.

【0022】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、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 entire incineration ash and does not cause clogging or the like, and has a combustion form suitable for melting. .

【0023】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。
Combustion of waste plastics by such means requires little coke and reduces coke by 10%.
Even with 0% replacement, our experiments were successful. However, use of coke as a heat source is not denied.

【0024】そして、該溶融スラグGは、ロストル26
の孔を通して滴下し、ガス分解室22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25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。
Then, the molten slag G is supplied to the Rostor 26
And is stored at the bottom of the gas decomposition chamber 22 and acts as a molten slag for keeping the gas decomposition chamber at a high temperature. Then, it flows down from the discharge port 25 and is transferred to the original pulverization processing and the like. It is. This step is sequentially repeated.

【0025】尚、本発明装置の処理対象物としては、ロ
ータリーキルン式焼却炉から排出される焼却灰であれ
ば、製鉄スラッジ、ガラス屑、金属スラッジ、金属屑等
その種類を問わず広く応用が可能である。
The object to be treated by the apparatus of the present invention can be widely applied to any kind of incineration ash discharged from a rotary kiln incinerator, such as steelmaking sludge, glass scrap, metal sludge, and metal scrap. It is.

【0026】[0026]

【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)油泥、タール、ピッチ、塗料等の粘稠物、染料か
す等の粉・粒状物等幅広い種類のゴミを焼却処理できる
ロータリーキルン式焼却炉にあって、そこから生成され
る焼却灰を溶融処理するに際し、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) Rotary kiln-type incinerators capable of incinerating a wide variety of garbage, such as oily mud, tar, pitch, paint, and other viscous materials, dye scum, and other powder and granular materials, and melt the incineration ash generated therefrom In the process, all can be replaced with waste plastic without using much coke as a heat source, so that the energy cost can be greatly reduced and the plastic that is in need of disposal as waste is used. Therefore, it is desirable from the viewpoint of resource utilization.

【0027】(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 form 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.

【0028】(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.

【0029】(4)ローラリーキルン式焼却炉から生成
される粉状の焼却灰を、粘結剤等で塊状に処理すること
なく、そのまま溶融炉に連結させることができるので、
工程面での省力化が可能となる。
(4) Since the powdery incineration ash generated from the roller-lee kiln incinerator can be directly connected to the melting furnace without being treated in a lump with a binder or the like,
Labor saving in the process becomes possible.

【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.

【図2】本発明装置の要部拡大断面図。FIG. 2 is an enlarged sectional view of a main part of the device of the present invention.

【符号の説明】[Explanation of symbols]

10 ロータリーキルン式焼却炉部 11 ゴミ貯留槽 12 定量供給装置 13 キルン本体 14 駆動部 15 空気導入口 16 始動用バーナ 17 排出口 20 溶融炉部 21 溶融炉 22 ガス分解室 23 搬送空気導入口 24 バーナー 25 排出口 26 ロストル 27 燃焼溶融室 28 二次空気導入口 29 酸素富化器 30 予備加熱室 31 炉頭部 40 廃棄プラスチック導入部 41 搬送管 42 ホッパー 43 定量供給機 44 ブロワー DESCRIPTION OF SYMBOLS 10 Rotary kiln type incinerator part 11 Garbage storage tank 12 Quantitative supply device 13 Kiln main body 14 Drive part 15 Air inlet 16 Starter burner 17 Discharge port 20 Melting furnace part 21 Melting furnace 22 Gas decomposition chamber 23 Transport air inlet 24 Burner 25 Discharge port 26 Rostor 27 Combustion and melting chamber 28 Secondary air inlet 29 Oxygen enricher 30 Preheating chamber 31 Furnace head 40 Waste plastic introduction section 41 Conveyor pipe 42 Hopper 43 Quantitative feeder 44 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 AA08 AA16 AB02 AB03 AC03 AC13 CA01 CA08 DA15 DB16 DB20 FA02 FA10 FA26 KA02 KA15 KA27 NB03 NB08 NB27 4D004 AA07 AA11 AA12 AA36 CA29 CB01 CB09 CB34 CB47 CC17 DA02 DA06  ────────────────────────────────────────────────── ─── 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 AA08 AA16 AB02 AB03 AC03 AC13 CA01 CA08 DA15 DB16 DB20 FA02 FA10 FA26 KA02 KA15 KA27 NB03 NB08 NB27 4D004 AA07 AA11 AA12 AA36 CA29 CB01 CB09 CB34 CB47 CC17 DA02 DA06

Claims (3)

【特許請求の範囲】[Claims] 【請求項1】 円筒形のキルンを軸心回りに回転させ、
その内部に燃焼空気を送り込んで燃焼室を形成して成る
ロータリーキルン式焼却炉から生成される焼却灰の排出
口に連結させて溶融炉を形成し、 該溶融炉を、 (a)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、 (b)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、 (c)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
燃焼溶融室に焼却灰を導いて溶融処理するようにしたこ
とを特徴とする溶融処理装置。
1. Rotating a cylindrical kiln about an axis,
A combustion furnace is formed by feeding combustion air into the inside of the furnace and connected to an outlet of incineration ash generated from a rotary kiln-type incinerator formed by forming a combustion chamber. And a gas decomposition chamber in which a fixed space for thermally decomposing the waste plastic by temporarily retaining the molten slag is disposed. (B) The waste plastic is disposed in a part of the gas decomposition chamber. (C) A rooster for raising the decomposition gas and dripping molten slag is disposed at the upper part of the gas decomposition chamber, and an air introduction port for promoting the combustion with the decomposition gas. A melting treatment apparatus characterized by forming a combustion melting chamber facing the combustion chamber, and guiding incineration ash to the combustion melting chamber for melting processing.
【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.
JP37726099A 1999-12-29 1999-12-29 Device for fusing incinerated ash, coupled with rotary kiln incinerator Pending JP2001193920A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP37726099A JP2001193920A (en) 1999-12-29 1999-12-29 Device for fusing incinerated ash, coupled with rotary kiln incinerator

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP37726099A JP2001193920A (en) 1999-12-29 1999-12-29 Device for fusing incinerated ash, coupled with rotary kiln incinerator

Publications (1)

Publication Number Publication Date
JP2001193920A true JP2001193920A (en) 2001-07-17

Family

ID=18508526

Family Applications (1)

Application Number Title Priority Date Filing Date
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Country Status (1)

Country Link
JP (1) JP2001193920A (en)

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US6954078B2 (en) 2001-08-10 2005-10-11 Centro De Pesquisas Renato Archer-Cenpra (Mct) Transparent tablet for evaluation of motor responses
JP2011174628A (en) * 2010-02-23 2011-09-08 Ngk Insulators Ltd Incineration method of waste ion exchange resin
CN115560336A (en) * 2022-10-13 2023-01-03 广东广业投资集团有限公司 Hazardous waste incineration ash on-line melting system and method and roadbed material

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US6954078B2 (en) 2001-08-10 2005-10-11 Centro De Pesquisas Renato Archer-Cenpra (Mct) Transparent tablet for evaluation of motor responses
JP2011174628A (en) * 2010-02-23 2011-09-08 Ngk Insulators Ltd Incineration method of waste ion exchange resin
CN115560336A (en) * 2022-10-13 2023-01-03 广东广业投资集团有限公司 Hazardous waste incineration ash on-line melting system and method and roadbed material

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