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JPH11148622A - Waste thermal decombustion gassifying/melting apparatus - Google Patents

Waste thermal decombustion gassifying/melting apparatus

Info

Publication number
JPH11148622A
JPH11148622A JP33081497A JP33081497A JPH11148622A JP H11148622 A JPH11148622 A JP H11148622A JP 33081497 A JP33081497 A JP 33081497A JP 33081497 A JP33081497 A JP 33081497A JP H11148622 A JPH11148622 A JP H11148622A
Authority
JP
Japan
Prior art keywords
waste
external heat
furnace
gas
pyrolysis
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
JP33081497A
Other languages
Japanese (ja)
Other versions
JP3876502B2 (en
Inventor
Mikio Mogi
幹夫 茂木
Yuichi Tago
祐一 田子
Munetaka Hagitani
宗高 萩谷
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.)
IHI Corp
Original Assignee
IHI 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 IHI Corp filed Critical IHI Corp
Priority to JP33081497A priority Critical patent/JP3876502B2/en
Publication of JPH11148622A publication Critical patent/JPH11148622A/en
Application granted granted Critical
Publication of JP3876502B2 publication Critical patent/JP3876502B2/en
Anticipated expiration legal-status Critical
Expired - Fee Related legal-status Critical Current

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  • Gasification And Melting Of Waste (AREA)
  • Incineration Of Waste (AREA)

Abstract

PROBLEM TO BE SOLVED: To take out thermally decomposed gas produced in an external heat kiln furnace as high calory gas with low hydrogen chloride concentration so as to obtain a higher evaluation for usage. SOLUTION: A ventilating dryer 18 is provided on an upstream side of an external heat kiln furnace 1 for previously drying waste 6. A lime powder charge line 20 for charging lime powder is provided on the ventilating dryer 18. A recovery line 25 for thermally decomposed gas 6a is connected in a hot gas producing furnace 9 for feeding high temperature gas 10 to the external heat kiln furnace 1. Hydrogen chloride produced by drying the waste 6 with the ventilating dryer is solidified with a reaction with the lime powder, and is removed to the outside of the system. The waste 6 after dried is thermally decomposed in the external heat kiln furnace 1, and the thermally decomposed gas 6a is fed to a hot gas producing furnace 9.

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】本発明は都市ごみなどの廃棄
物を熱分解ガス化すると共に熱分解残渣を溶融させるよ
うにした廃棄物熱分解ガス化溶融装置に関するものであ
る。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a waste pyrolysis gasification and melting apparatus for pyrolyzing waste such as municipal waste and melting a pyrolysis residue.

【0002】[0002]

【従来の技術】現在の廃棄物の処理方式としては、焼却
炉にて廃棄物を燃焼するようにした燃焼方式が採用され
ている。
2. Description of the Related Art As a current waste disposal system, a combustion system in which waste is burned in an incinerator is employed.

【0003】しかしながら、上記燃焼方式の場合には、
燃焼排ガス中に含まれるダイオキシン発生の問題があ
ること、ガス量が多く熱エネルギーの利用効率が悪い
こと、灰が多量に出るのでその処理が大変であるこ
と、埋立地の容量が限界に近付いてきていること、等
の問題が提起されている。
[0003] However, in the case of the above-mentioned combustion system,
There is a problem of dioxin generation in the flue gas, the amount of gas is large, the efficiency of using heat energy is inefficient, the ash is generated in large quantities, the treatment is difficult, and the capacity of landfills is approaching its limit. Issues have been raised.

【0004】そのため、次世代の廃棄物処理方式とし
て、廃棄物を不活性雰囲気下で加熱して熱分解し、発生
した熱分解ガスと熱分解残渣(チャー)を溶融炉で空気
比1.3程度の少ない空気量で高温にして燃焼させ、廃
棄物中の灰分を溶融スラグとして取り出すようにしたガ
ス化・溶融方式が開発され、一部で実証運転が行われて
いる。かかる方式では、廃棄物を熱分解ガス化するため
に、外熱キルン方式を採用し、外部からの熱で廃棄物を
間接的に加熱、乾燥させて熱分解させるようにしてい
る。
Therefore, as a next-generation waste treatment method, waste is heated and pyrolyzed in an inert atmosphere, and the generated pyrolysis gas and pyrolysis residue (char) are melted at an air ratio of 1.3 in a melting furnace. A gasification and melting system has been developed in which ash in waste is taken out as molten slag by burning at a high temperature with a small amount of air, and demonstration operation has been performed in some of them. In such a method, an external heat kiln is used to thermally decompose the waste into gas, and the waste is indirectly heated and dried by heat from the outside to be thermally decomposed.

【0005】廃棄物を熱分解ガス化・溶融するために用
いられている熱分解ガス化溶融装置は、図2にその一例
の概要を示す如く、一端の入口2側よりも他端の出口3
側を約3度低くなるように傾斜させて横向きに配置した
ロータリー型の外熱キルン炉1の長手方向一端の入口2
に、給じん機4を設けて投入ホッパ5から廃棄物6を投
入するようにすると共に、上記外熱キルン炉1の長手方
向他端の出口3に、熱分解ガス6aと熱分解残渣6bと
を分離する分離室7を設け、外熱キルン炉1を低速で回
転させた状態において、投入ホッパ5内から投入された
廃棄物6を給じん機4によって外熱キルン炉1内に徐々
に供給しつつ、外側の加熱流路8内に、熱回収空気13
や補助燃料12を用いて熱風発生炉9で発生させた高温
ガス(熱風)10を、高温ガス送給ライン11を通し出
口3側から入口2側へ向け流通させて燃焼排ガスライン
17より排出させることにより、外熱キルン炉1内の廃
棄物6を加熱、乾燥させて熱分解し、発生した熱分解ガ
ス6aを、出口3部の分離室7の上部に接続した熱分解
ガス取出ライン14を通して下流の溶融炉15に送るよ
うにし、一方、金属類を含む熱分解残渣6bを、金属類
6dを回収してから熱分解残渣ライン16により上記溶
融炉15へ送り、更に1300℃以上で高温燃焼させて
溶融スラグ6cとして取り出すようにしてある。なお、
外熱キルン炉1の燃焼排ガス10aは、ファン30によ
り熱風発生炉9へ循環させ、その余剰分は溶融炉15の
排ガス出口部に導くようにしてある。
As shown in FIG. 2, a pyrolysis gasification / melting apparatus used for pyrolysis gasification and melting of wastes has an outlet 3 at one end rather than an inlet 2 at one end.
Inlet 2 at one end in the longitudinal direction of a rotary type external heat kiln furnace 1 arranged sideways with its side inclined at about 3 degrees lower
In addition, a dust feeder 4 is provided so that waste 6 is charged from a charging hopper 5, and a pyrolysis gas 6 a and a pyrolysis residue 6 b are provided to an outlet 3 at the other end in the longitudinal direction of the external heat kiln 1. A separation chamber 7 for separating the wastewater is provided, and in a state where the external heat kiln furnace 1 is rotated at a low speed, the waste 6 charged from the charging hopper 5 is gradually supplied into the external heat kiln furnace 1 by the duster 4. While the heat recovery air 13
The hot gas (hot air) 10 generated in the hot-air generating furnace 9 using the gas and the auxiliary fuel 12 flows through the high-temperature gas supply line 11 from the outlet 3 side to the inlet 2 side, and is discharged from the combustion exhaust gas line 17. Thereby, the waste 6 in the external heat kiln 1 is heated, dried, and thermally decomposed, and the generated pyrolysis gas 6a is passed through a pyrolysis gas extraction line 14 connected to the upper part of the separation chamber 7 at the three outlets. It is sent to the downstream melting furnace 15, and on the other hand, the pyrolysis residue 6 b containing metals is recovered to the melting furnace 15 through the pyrolysis residue line 16 after recovering the metals 6 d, and further burned at a high temperature of 1300 ° C. or more. Then, the molten slag 6c is taken out. In addition,
The combustion exhaust gas 10 a of the external heat kiln 1 is circulated to the hot air generator 9 by the fan 30, and the surplus is guided to the exhaust gas outlet of the melting furnace 15.

【0006】[0006]

【発明が解決しようとする課題】ところが、上記熱分解
ガス化溶融装置の場合、ポリ塩化ビニル等のプラスチッ
ク類を比較的多く含む廃棄物を熱分解すると、熱分解ガ
ス6a中の塩化水素濃度が高くなり、又、廃棄物6が保
有する水分量が多いと熱分解ガス6aの水分も多くなる
ので、熱分解ガス6aを、塩化水素濃度が低く且つ高カ
ロリーのガスとして取り出すことができなかった。更
に、これまでは、熱分解ガス6aを外熱キルン炉1の熱
源として使用しようとしても、発熱量が低く塩化水素が
腐食源となることから、使用することは難しかった。
However, in the case of the above-mentioned pyrolysis gasification and melting apparatus, when waste containing a relatively large amount of plastics such as polyvinyl chloride is pyrolyzed, the concentration of hydrogen chloride in the pyrolysis gas 6a is reduced. If the amount of water contained in the waste 6 is large, the moisture of the pyrolysis gas 6a also increases, so that the pyrolysis gas 6a cannot be taken out as a gas having a low hydrogen chloride concentration and a high calorie. . Further, it has been difficult to use the pyrolysis gas 6a as a heat source of the external heat kiln furnace 1 because the calorific value is low and hydrogen chloride is a corrosion source.

【0007】そこで、本発明は、外熱キルン炉で生成さ
れた熱分解ガスを、塩化水素濃度が低く且つ高カロリー
のガスとして取り出すことができるようにし、更に、熱
分解ガスを外熱キルン炉の熱源として有効に利用できる
ようにしようとするものである。
In view of the above, the present invention enables the pyrolysis gas generated in an external heat kiln furnace to be extracted as a gas having a low hydrogen chloride concentration and a high calorie. It is intended to make it possible to use it effectively as a heat source.

【0008】[0008]

【課題を解決するための手段】本発明は、上記課題を解
決するために、外熱キルン炉内の廃棄物を熱風発生炉で
発生させた高温ガスを熱源として乾燥、熱分解し、熱分
解ガス及び熱分解残渣を下流の溶融炉へ送って処理する
ようにしてある廃棄物熱分解ガス化溶融装置において、
上記外熱キルン炉の上流側に、該外熱キルン炉に供給す
る前の廃棄物を乾燥させるための通気乾燥機を設置し、
且つ該通気乾燥機に石灰粉を投入できるようにし、更
に、上記通気乾燥機の排気ラインに集じん器を設置した
構成とする。
SUMMARY OF THE INVENTION In order to solve the above-mentioned problems, the present invention provides a method of drying and thermally decomposing waste in an external heat kiln using a high-temperature gas generated in a hot-air generating furnace as a heat source. In a waste pyrolysis gasification and melting apparatus, which is configured to send gas and pyrolysis residue to a downstream melting furnace for processing,
On the upstream side of the external heat kiln furnace, a through-air dryer for drying waste before being supplied to the external heat kiln furnace is installed,
In addition, lime powder can be introduced into the through-air dryer, and a dust collector is installed in an exhaust line of the through-air dryer.

【0009】通気乾燥機内に石灰粉投入ラインにより石
灰粉を投入すると、乾燥段階で発生した塩化水素がアル
カリ金属塩として固定され、集じん器で捕集されること
により系外に除去される。又、一部の石灰粉は外熱キル
ン炉にごみとともに送られ熱分解段階で発生したHCl
を熱分解残渣側に固定する。一方、廃棄物は多くの水分
が除去されてから外熱キルン炉に供給されるため、熱分
解ガス中の水分量を少なくすることができる。したがっ
て、熱分解ガスを、塩化水素濃度が低く且つ高カロリー
のガスとして取り出すことができるようになる。
When lime powder is introduced into the through-air dryer through a lime powder introduction line, hydrogen chloride generated in the drying stage is fixed as an alkali metal salt, and is removed from the system by being collected by a dust collector. Also, some lime powder is sent to the external heat kiln furnace together with the refuse and HCl generated in the pyrolysis stage.
To the pyrolysis residue side. On the other hand, the waste is supplied to the external heat kiln furnace after a large amount of water is removed, so that the amount of water in the pyrolysis gas can be reduced. Therefore, the pyrolysis gas can be taken out as a gas having a low hydrogen chloride concentration and a high calorie.

【0010】又、外熱キルン炉内での熱分解により生成
された熱分解ガスの回収ラインを、熱風発生炉に導設し
た構成とすることにより、塩化水素濃度が低く且つ高カ
ロリーの熱分解ガスが熱風発生炉を介して外熱キルン炉
に導かれるので、腐食の心配を起すことなく外熱キルン
炉の熱源とすることができる。
[0010] In addition, the recovery line for the pyrolysis gas generated by the pyrolysis in the external heat kiln furnace is provided to the hot blast furnace, so that the hydrogen chloride concentration is low and the high-calorie pyrolysis is performed. Since the gas is led to the external heat kiln furnace through the hot air generating furnace, it can be used as a heat source of the external heat kiln furnace without causing a concern about corrosion.

【0011】[0011]

【発明の実施の形態】以下、本発明の実施の形態を図面
を参照して説明する。
Embodiments of the present invention will be described below with reference to the drawings.

【0012】図1は本発明の実施の一形態を示すもの
で、図2に示したと同様な構成において、外熱キルン炉
1の上流側に、該外熱キルン炉1に供給する前の廃棄物
6を乾燥させるための通気乾燥機18を前処理装置とし
て設置すると共に、該通気乾燥機18に、外熱キルン炉
1の燃焼排ガスライン17を接続して、外熱キルン炉1
での廃棄物6の熱分解に供した後の燃焼排ガス10aを
通気乾燥機18の乾燥熱源として導けるようにし、且つ
上記通気乾燥機18の給じん機19(又は燃焼排ガスラ
イン17)に、消石灰や生石灰粉等の石灰粉を投入する
ための石灰粉投入ライン20を設けて、廃棄物6の乾燥
段階で発生した塩化水素(Cl)をアルカリ金属塩(C
aCl2 )の固体とさせられるようにし、更に、上記通
気乾燥機18の排気ライン21を熱風発生炉9と溶融炉
15の排ガス出口部22に分岐させて導設し、該排気ラ
イン21の途中に集じん器23を設置して、通気乾燥機
18から排出させられた乾燥排ガス10b中に含む塩素
のアルカリ金属塩を集じん器23で捕集して系外に除去
できるようにする。
FIG. 1 shows an embodiment of the present invention. In a configuration similar to that shown in FIG. 2, a waste before being supplied to the external heat kiln furnace 1 is disposed upstream of the external heat kiln furnace 1. A ventilation dryer 18 for drying the object 6 is installed as a pretreatment device, and a flue gas line 17 of the external heat kiln furnace 1 is connected to the ventilation dryer 18 so that the external heat kiln 1
The flue gas 10a after being subjected to the thermal decomposition of the waste 6 is guided as a drying heat source for the through-air dryer 18 and slaked lime is supplied to the duster 19 (or the flue gas line 17) of the through-air dryer 18. A lime powder input line 20 for inputting lime powder such as lime powder or quick lime powder is provided to convert hydrogen chloride (Cl) generated in the drying stage of the waste 6 into an alkali metal salt (C).
aCl 2 ), and the exhaust line 21 of the through-air dryer 18 is branched and introduced into the hot-air generating furnace 9 and the exhaust gas outlet 22 of the melting furnace 15. A dust collector 23 is installed in the dust collector 23 so that the alkali metal salt of chlorine contained in the dried exhaust gas 10b discharged from the through-air dryer 18 can be collected by the dust collector 23 and removed outside the system.

【0013】又、上記外熱キルン炉1の分離室7と下流
側の溶融炉15との間に接続された熱分解ガス取出ライ
ン14の途中に、集じん器24を介在設置し、該集じん
器24の下流側に位置する熱分解ガス取出ライン14の
途中から回収ライン25を分岐させて、該回収ライン2
5を熱風発生炉9に導設し、集じん器24を通過した後
の熱分解ガス6aを熱風発生炉9に供給できるように
し、更に、上記集じん器25と熱分解残渣ライン16と
の間に、集じん器24で捕集した熱分解残渣6bを熱分
解残渣ライン16に戻すための戻しライン26を設け
る。
In addition, a dust collector 24 is installed in the middle of a pyrolysis gas extraction line 14 connected between the separation chamber 7 of the external heat kiln furnace 1 and the downstream melting furnace 15. The recovery line 25 is branched from the middle of the pyrolysis gas extraction line 14 located on the downstream side of the
5 is introduced into the hot air generator 9 so that the pyrolysis gas 6 a after passing through the dust collector 24 can be supplied to the hot air generator 9. In between, a return line 26 for returning the pyrolysis residue 6b collected by the dust collector 24 to the pyrolysis residue line 16 is provided.

【0014】なお、27は高温ガス送給ライン11に設
けた温度制御器28からの指令で開閉制御されるように
回収ライン25中に設けた開閉制御弁を示す。31は熱
分解ガス用のファンを示す。
Reference numeral 27 denotes an open / close control valve provided in the recovery line 25 so as to be opened / closed by a command from a temperature controller 28 provided in the high-temperature gas supply line 11. Reference numeral 31 denotes a fan for pyrolysis gas.

【0015】上記構成としてある本発明の廃棄物熱分解
ガス化溶融装置では、外熱キルン炉1で廃棄物6を加
熱、乾燥して熱分解させる前に、通気乾燥機18で廃棄
物6を乾燥させて50%程度の水分を除去し、乾燥後の
廃棄物6を外熱キルン炉1に供給するようにさせる。
In the waste pyrolysis gasification and melting apparatus of the present invention having the above-mentioned structure, the waste 6 is heated and dried in the external heat kiln 1 before being thermally decomposed. It is dried to remove about 50% of water, and the dried waste 6 is supplied to the external heat kiln furnace 1.

【0016】上記の場合、熱風発生炉9で発生させた高
温ガス10を、高温ガス送給ライン11を通し外熱キル
ン炉1の加熱流路8に流通させるようにして運転を行う
と、運転中は、外熱キルン炉1での廃棄物6の熱分解に
供した後の燃焼排ガス10aが通気乾燥機18の熱源と
して燃焼排ガスライン17を通り通気乾燥機18に供給
される。
In the above case, when the operation is performed such that the high-temperature gas 10 generated in the hot-air generating furnace 9 is passed through the high-temperature gas supply line 11 to the heating flow path 8 of the external heat kiln furnace 1, During the combustion, the combustion exhaust gas 10 a after being subjected to the thermal decomposition of the waste 6 in the external heat kiln furnace 1 is supplied to the ventilation dryer 18 through the combustion exhaust gas line 17 as a heat source of the ventilation dryer 18.

【0017】上記通気乾燥機18では、供給された燃焼
排ガス10aによって直接接触加熱により廃棄物6が乾
燥させられるが、この際、通気乾燥機18内には、石灰
粉投入ライン20を通して石灰粉が投入された状態にあ
るため、乾燥段階で廃棄物6から発生する塩化水素(C
l)は反応によりアルカリ金属塩(CaCl2 )の固体
とされ、更に、このアルカリ金属塩の固体は、排気ライ
ン21を通り集じん器23で捕集されるため、系外に除
去することができる。
In the through-air dryer 18, the waste 6 is dried by direct contact heating with the supplied combustion exhaust gas 10 a. At this time, the lime powder passes through the lime-powder input line 20 in the through-air dryer 18. Since it is in the charged state, hydrogen chloride (C) generated from the waste 6 in the drying stage
l) is converted into a solid of an alkali metal salt (CaCl 2 ) by the reaction, and the solid of the alkali metal salt is collected by a dust collector 23 through an exhaust line 21, so that the solid can be removed outside the system. it can.

【0018】一方、通気乾燥機18で乾燥させられた廃
棄物6は、次に、外熱キルン炉1に供給されることにな
るため、外熱キルン炉1では、多くの水分が除去された
廃棄物6を熱分解するので、熱分解ガス6a内の水分量
も少なくなり、高カロリーのガスを取り出すことができ
るようになる。この際、外熱キルン炉1内でも、熱分解
段階で塩化水素が多少発生するが、通気乾燥機18から
は未反応の石灰粉も同時に供給されることから、発生し
た塩化水素を熱分解残渣6b側に固定することができ
る。したがって、塩化水素濃度が最小値となった高カロ
リーの熱分解ガス6aを取り出すことができる。
On the other hand, the waste 6 dried by the through-air drier 18 is then supplied to the external heat kiln furnace 1, and in the external heat kiln 1, much water has been removed. Since the waste 6 is thermally decomposed, the amount of water in the pyrolysis gas 6a is also reduced, and a high-calorie gas can be taken out. At this time, even in the external heat kiln furnace 1, some hydrogen chloride is generated in the pyrolysis stage, but unreacted lime powder is also supplied from the through-air dryer 18. 6b side. Therefore, the high-calorie pyrolysis gas 6a having the minimum hydrogen chloride concentration can be taken out.

【0019】更に、この熱分解ガス6aは、熱分解ガス
取出ライン14から回収ライン25を経て熱風発生炉9
に供給されるため、熱分解ガス6aを、腐食の心配なく
外熱キルン炉1の熱源として有効に使用することができ
ることになる。
Further, the pyrolysis gas 6a is supplied from the pyrolysis gas extraction line 14 through the recovery line 25 to the hot air generating furnace 9.
Therefore, the pyrolysis gas 6a can be effectively used as a heat source of the external heat kiln furnace 1 without fear of corrosion.

【0020】なお、上記通気乾燥機18で廃棄物6の乾
燥に供した後の乾燥排ガス10bは臭気成分を含んでい
るが、排気ライン21を通り溶融炉15の排ガス出口部
22に導かれるため、ここで、1300℃以上の高温の
溶融排ガス29に混入されることにより、高温分解させ
られて排出される。
Although the dried exhaust gas 10b after drying the waste 6 by the through-air dryer 18 contains an odorous component, it is led to the exhaust gas outlet 22 of the melting furnace 15 through the exhaust line 21. Here, by being mixed into the molten exhaust gas 29 having a high temperature of 1300 ° C. or more, it is decomposed and discharged at a high temperature.

【0021】[0021]

【発明の効果】以上述べた如く、本発明によれば、次の
如き優れた効果を発揮する。 (1) 外熱キルン炉内の廃棄物を熱風発生炉で発生させた
高温ガスを熱源として乾燥、熱分解し、熱分解ガス及び
熱分解残渣を下流の溶融炉へ送って処理するようにして
ある廃棄物熱分解ガス化溶融装置において、上記外熱キ
ルン炉の上流側に、該外熱キルン炉に供給する前の廃棄
物を乾燥させるための通気乾燥機を設置し、且つ該通気
乾燥機に石灰粉を投入できるようにし、更に、上記通気
乾燥機の排気ラインに集じん器を設置した構成としてあ
るので、通気乾燥機内に投入する石灰粉により、乾燥段
階で発生した塩化水素をアルカリ金属塩として固定し、
集じん器で捕集して系外に除去することができ、一方、
多くの水分を除去した後の廃棄物を外熱キルン炉で熱分
解することから、熱分解ガス中の水分量を少なくするこ
とができ、しかも通気乾燥機で未反応の石灰粉も外熱キ
ルン炉に供給されることで、熱分解段階で発生する塩化
水素を熱分解残渣側に固定することができ、したがっ
て、塩化ガス水素濃度が低く且つ高カロリーの熱分解ガ
スを取り出すことができることにより、熱分解ガスの利
用価値を高めることができる。 (2) 外熱キルン炉内での熱分解により生成された熱分解
ガスの回収ラインを、熱風発生炉に導設した構成とする
ことにより、塩化水素濃度が低く且つ高カロリーの熱分
解ガスを熱風発生炉に導くことができるので、熱分解ガ
スを、腐食の心配を起すことなく外熱キルン炉の熱源と
して有効に使用することができる。
As described above, according to the present invention, the following excellent effects are exhibited. (1) The waste in the external heat kiln furnace is dried and pyrolyzed using the high-temperature gas generated in the hot air generator as the heat source, and the pyrolysis gas and pyrolysis residue are sent to the downstream melting furnace for processing. In a waste pyrolysis gasification / melting apparatus, a ventilation dryer for drying waste before being supplied to the external heat kiln furnace is installed upstream of the external heat kiln furnace, and the ventilation dryer is Lime powder can be fed into the air dryer, and a dust collector is installed in the exhaust line of the above-mentioned through-air dryer. Fixed as salt,
It can be collected by a dust collector and removed outside the system, while
The waste from which much water has been removed is pyrolyzed in an external heat kiln furnace, which reduces the amount of moisture in the pyrolysis gas. By being supplied to the furnace, the hydrogen chloride generated in the pyrolysis stage can be fixed to the pyrolysis residue side, and therefore, the hydrogen chloride gas concentration is low and a high calorie pyrolysis gas can be taken out. The utility value of the pyrolysis gas can be increased. (2) By adopting a configuration in which a recovery line for pyrolysis gas generated by pyrolysis in an external heat kiln furnace is introduced to a hot air generation furnace, a low hydrogen chloride concentration and high calorie pyrolysis gas can be obtained. Since the gas can be led to the hot-air generating furnace, the pyrolysis gas can be effectively used as a heat source of the externally-heated kiln furnace without causing a fear of corrosion.

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

【図1】本発明の廃棄物熱分解ガス化溶融装置の実施の
一形態を示す概要図である。
FIG. 1 is a schematic diagram showing one embodiment of a waste pyrolysis gasification and melting apparatus of the present invention.

【図2】廃棄物熱分解ガス化溶融装置の一例を示す概要
図である。
FIG. 2 is a schematic diagram illustrating an example of a waste pyrolysis gasification and melting apparatus.

【符号の説明】[Explanation of symbols]

1 外熱キルン炉 6 廃棄物 6a 熱分解ガス 6b 熱分解残渣 6c 溶融スラグ 8 加熱流路 9 熱風発生炉 10 高温ガス 10a 燃焼排ガス 18 通気乾燥機 20 石灰粉投入ライン 21 排気ライン 23 集じん器 25 回収ライン DESCRIPTION OF SYMBOLS 1 External heat kiln furnace 6 Waste 6a Pyrolysis gas 6b Pyrolysis residue 6c Melt slag 8 Heating path 9 Hot air generator 10 High temperature gas 10a Combustion exhaust gas 18 Ventilation dryer 20 Lime powder input line 21 Exhaust line 23 Dust collector 25 Collection line

───────────────────────────────────────────────────── フロントページの続き (51)Int.Cl.6 識別記号 FI F23G 5/20 ZAB F23G 5/20 ZABA F23J 1/00 F23J 1/00 B (72)発明者 萩谷 宗高 東京都江東区豊洲三丁目1番15号 石川島 播磨重工業株式会社東二テクニカルセンタ ー内────────────────────────────────────────────────── ─── Continued on the front page (51) Int.Cl. 6 Identification code FI F23G 5/20 ZAB F23G 5/20 ZABA F23J 1/00 F23J 1/00 B (72) Inventor Munetaka Hagiya Toyosu, Koto-ku, Tokyo 3-1-1-15 Ishikawajima Harima Heavy Industries, Ltd.

Claims (2)

【特許請求の範囲】[Claims] 【請求項1】 外熱キルン炉内の廃棄物を熱風発生炉で
発生させた高温ガスを熱源として乾燥、熱分解し、熱分
解ガス及び熱分解残渣を下流の溶融炉へ送って処理する
ようにしてある廃棄物熱分解ガス化溶融装置において、
上記外熱キルン炉の上流側に、該外熱キルン炉に供給す
る前の廃棄物を乾燥させるための通気乾燥機を設置し、
且つ該通気乾燥機に石灰粉を投入できるようにし、更
に、上記通気乾燥機の排気ラインに集じん器を設置した
構成を有することを特徴とする廃棄物熱分解ガス化溶融
装置。
1. A method of drying and thermally decomposing waste in an external heat kiln furnace using a high-temperature gas generated in a hot air generating furnace as a heat source, and sending a pyrolysis gas and a pyrolysis residue to a downstream melting furnace for processing. In the waste pyrolysis gasification and melting equipment that has been
On the upstream side of the external heat kiln furnace, a through-air dryer for drying waste before being supplied to the external heat kiln furnace is installed,
A waste pyrolysis gasification / melting apparatus characterized in that lime powder can be introduced into the through-air dryer and a dust collector is installed in an exhaust line of the through-air dryer.
【請求項2】 外熱キルン炉内での熱分解により生成さ
れた熱分解ガスの回収ラインを、熱風発生炉に導設した
請求項1記載の廃棄物熱分解ガス化溶融装置。
2. The waste pyrolysis gasification and melting apparatus according to claim 1, wherein a recovery line for the pyrolysis gas generated by the pyrolysis in the external heat kiln furnace is installed in the hot air generation furnace.
JP33081497A 1997-11-17 1997-11-17 Waste pyrolysis gasification melting equipment Expired - Fee Related JP3876502B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP33081497A JP3876502B2 (en) 1997-11-17 1997-11-17 Waste pyrolysis gasification melting equipment

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP33081497A JP3876502B2 (en) 1997-11-17 1997-11-17 Waste pyrolysis gasification melting equipment

Publications (2)

Publication Number Publication Date
JPH11148622A true JPH11148622A (en) 1999-06-02
JP3876502B2 JP3876502B2 (en) 2007-01-31

Family

ID=18236853

Family Applications (1)

Application Number Title Priority Date Filing Date
JP33081497A Expired - Fee Related JP3876502B2 (en) 1997-11-17 1997-11-17 Waste pyrolysis gasification melting equipment

Country Status (1)

Country Link
JP (1) JP3876502B2 (en)

Also Published As

Publication number Publication date
JP3876502B2 (en) 2007-01-31

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