JP2008082563A - Waste melting furnace and operation method of waste melting furnace - Google Patents

Waste melting furnace and operation method of waste melting furnace Download PDF

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JP2008082563A
JP2008082563A JP2006259900A JP2006259900A JP2008082563A JP 2008082563 A JP2008082563 A JP 2008082563A JP 2006259900 A JP2006259900 A JP 2006259900A JP 2006259900 A JP2006259900 A JP 2006259900A JP 2008082563 A JP2008082563 A JP 2008082563A
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furnace
dust
waste
melting furnace
ash
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JP4918833B2 (en
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Koji Kasuya
幸司 粕谷
Tsuneo Matsudaira
恒夫 松平
Hajime Akiyama
肇 秋山
Tomohiro Yoshida
朋広 吉田
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JFE Engineering Corp
JFE Environmental Solutions Corp
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JFE Environmental Solutions Corp
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Abstract

<P>PROBLEM TO BE SOLVED: To provide a waste melting furnace and its operation method capable of performing melting treatment of dust generated from the waste melting furnace by blowing the same from a tuyere without blocking the tuyere and degrading a situation in the furnace. <P>SOLUTION: This waste melting furnace where a high-temperature combustion zone is formed at a lower portion of the furnace, a waste layer is formed at an upper part of the high-temperature combustion zone, the charged waste is thermally decomposed and its residues are melted, comprises the tuyere 13 for blowing an oxygen-containing gas to the high-temperature combustion zone, a sieve device 35 receiving the supply of dust discharged and collected from the waste melting furnace and sieving the same, devices 37, 39, 41, 43 for blowing the fine dust under the sieve from the tuyere, and a device 45 for charging the coarse dust on the sieve from a furnace top. <P>COPYRIGHT: (C)2008,JPO&INPIT

Description

本発明は、廃棄物を熱分解して残渣を溶融する廃棄物溶融炉及びその操業方法に関するものである。   The present invention relates to a waste melting furnace for thermally decomposing waste to melt residues, and an operation method thereof.

廃棄物を処理する技術として、都市ごみやシュレッダーダストなどの廃棄物を熱分解して可燃性ガスを発生させ、その熱分解残渣を溶融しスラグにして排出するガス化溶融処理がある。
この処理方法は廃棄物をガス化することによりその燃焼熱を回収することができるとともに、残渣を溶融して埋立処分など最終処分量を減容することができる利点を有している。
このような処理を行なう溶融炉には幾つかの方式によるものがあるが、その一つとして、シャフト式廃棄物ガス化溶融炉がある。
このシャフト式廃棄物ガス化溶融炉は、例えば、炉底部に堆積させたコークスを燃焼させ、この高温のコークス上へ廃棄物を投入して、熱分解させてガス化し、次いでその熱分解残渣を溶融してスラグにする処理を行なう方式の炉である(特許文献1参照)。
As a technology for treating waste, there is a gasification melting process in which waste such as municipal waste and shredder dust is pyrolyzed to generate a combustible gas, and the pyrolysis residue is melted and discharged as slag.
This treatment method has the advantage that the combustion heat can be recovered by gasifying the waste, and the final disposal amount such as landfill disposal can be reduced by melting the residue.
There are several types of melting furnaces for performing such treatment, and one of them is a shaft type waste gasification melting furnace.
In this shaft-type waste gasification and melting furnace, for example, coke deposited at the bottom of the furnace is burned, waste is put on this high-temperature coke, pyrolyzed and gasified, and then the pyrolysis residue is removed. It is a furnace of a system that performs a process of melting into slag (see Patent Document 1).

このようなシャフト式廃棄物ガス化溶融炉においては、炉体の機能が大別して縦方向に3つに区分されている。すなわち、炉底部にコークスを堆積させた高温燃焼帯が設けられ、この高温燃焼帯の上に廃棄物堆積層が設けられ、炉体の上部に大きな空間を有するフリーボード部が設けられている。   In such a shaft-type waste gasification and melting furnace, the functions of the furnace body are roughly divided into three in the vertical direction. That is, a high-temperature combustion zone in which coke is deposited at the bottom of the furnace is provided, a waste accumulation layer is provided on the high-temperature combustion zone, and a free board portion having a large space is provided above the furnace body.

そして、上記各部では酸素含有ガスの吹き込みが行われる。高温燃焼帯には主羽口が設けられ、投入されて堆積されたコークスを燃焼させて廃棄物の熱分解残渣を溶融するための酸素富化空気が吹き込まれる。また、廃棄物堆積層には副羽口が設けられ、投入されて堆積された廃棄物を部分燃焼させると共に廃棄物を緩やかに流動させながら熱分解させるための空気が吹き込まれる。また、フリーボード部には三段羽口が設けられ、廃棄物が熱分解されて生成した熱分解ガス(可燃性ガス)を部分燃焼させて内部を所定温度に維持するための空気が吹き込まれる。   And in each said part, oxygen-containing gas blowing is performed. A main tuyere is provided in the high-temperature combustion zone, and oxygen-enriched air is blown into the coke deposited and burned to melt the pyrolysis residue of the waste. In addition, the waste accumulation layer is provided with a sub tuyere, and air is blown in to thermally burn the waste deposited and partly burned and slowly flow the waste. In addition, the freeboard part is provided with a three-stage tuyere, and air is blown into the pyrolyzed gas (combustible gas) generated by pyrolyzing the waste to partially burn and maintain the interior at a predetermined temperature. .

このようにシャフト式廃棄物ガス化溶融炉は、廃棄物を、一つの炉で熱分解ガス化溶融処理する設備である。投入した廃棄物は熱分解され、ガスと残渣に分離される。ガスは可燃性ガスを多量に含み二次燃焼炉で燃焼され、ボイラやエコノマイザで熱回収された後、サイクロンで比較的粗いダストが除去され、減温装置で冷却され、有害ガスが除去され集塵機で除塵処理され放散される。また、熱分解残渣は、炉内を下方に移動し、炉下部のコークス高温燃焼帯で溶融され、スラグとメタルとして排出される。   As described above, the shaft-type waste gasification and melting furnace is a facility for performing pyrolytic gasification and melting treatment of waste in one furnace. The input waste is pyrolyzed and separated into gas and residue. The gas contains a large amount of combustible gas, burned in a secondary combustion furnace, recovered by heat with a boiler or economizer, removed relatively coarse dust with a cyclone, cooled with a temperature reducing device, removed harmful gas, and a dust collector Is dedusted and diffused. Further, the pyrolysis residue moves downward in the furnace, is melted in the coke high-temperature combustion zone at the lower part of the furnace, and is discharged as slag and metal.

ガス化溶融炉で発生したガスが二次燃焼炉、ボイラ、サイクロン、減温装置を経て集塵機へ到達するまでの間において、ガス中のダストのうち、比較的粗い粒子がそれぞれの装置内に落下する。このため、ガス化溶融炉と集塵機の間に配置された各装置内に落下したダスト(落下灰という)の抜出しが行なわれ、抜き出された落下灰は埋立処分されている。   Until the gas generated in the gasification and melting furnace reaches the dust collector via the secondary combustion furnace, boiler, cyclone, and temperature reducing device, relatively coarse particles of the gas fall into each device. To do. For this reason, dust (referred to as fall ash) that has fallen into each device arranged between the gasification melting furnace and the dust collector is extracted, and the extracted fall ash is disposed of in landfill.

なお、埋立処分場の負荷軽減のため埋立処分量を削減するという要望に対して、発生ダストをガス化溶融炉の羽口から吹き込み溶融してスラグ化することが試みられている(特許文献2参照)。
特許文献2では、ガス化溶融炉から飛散するダストをサイクロンなどの除塵機で捕集し、捕集したダストを羽口から炉内へ吹き込むようにしている。
特開平9−60830号公報 特開平8−285250号公報
Incidentally, in response to a request to reduce the amount of landfill disposal to reduce the load on the landfill disposal site, it has been attempted to blow and melt the generated dust from the tuyere of the gasification melting furnace to form slag (Patent Document 2). reference).
In Patent Document 2, dust scattered from the gasification melting furnace is collected by a dust remover such as a cyclone, and the collected dust is blown into the furnace from the tuyere.
Japanese Patent Laid-Open No. 9-60830 JP-A-8-285250

特許文献2のダスト処理方法においては、ガス化溶融炉の炉頂から飛散したダストを排ガス配管に設けられたサイクロンなどの除塵機で捕集し、捕集したダストはホッパーに一時的に貯留され切り出されて羽口から炉内へ吹き込まれる。
しかしながら、ダストには大粒径ダストやダストの大塊があり、羽口を閉塞したり、炉内に吹き込まれたとしても短時間で溶融せずに羽口先で滞留して、ガス流れを阻害したりして炉内状況を悪化させることがあるという問題がある。
In the dust treatment method of Patent Document 2, dust scattered from the top of the gasification melting furnace is collected by a dust remover such as a cyclone provided in the exhaust gas pipe, and the collected dust is temporarily stored in a hopper. It is cut out and blown into the furnace from the tuyere.
However, dust has large particle size dust and large lump of dust, and even if it is closed in the tuyere or blown into the furnace, it does not melt in a short time and stays at the tuyere tip to inhibit gas flow There is a problem that the situation inside the furnace may be worsened.

本発明は上記のような課題を解決するためになされたもので、羽口を閉塞したり、炉内状況を悪化させたりすることなく、廃棄物溶融炉から発生するダストを羽口から吹込み溶融処理できるようにした廃棄物溶融炉とその操業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-described problems, and dust generated from a waste melting furnace is blown from the tuyere without closing the tuyere or deteriorating the condition in the furnace. An object of the present invention is to provide a waste melting furnace capable of being melted and an operation method thereof.

(1)本発明に係る廃棄物溶融炉は、炉下部に高温燃焼帯が形成されて該高温燃焼帯の上方に廃棄物層が形成され、投入された廃棄物を熱分解すると共に残渣を溶融する廃棄物溶融炉であって、前記高温燃焼帯に酸素含有ガスを吹き込む羽口と、前記廃棄物溶融炉から排出されて回収されたダストの供給を受けて該ダストを細粒ダストと粗粒ダストに分級する分級装置と、細粒ダストを前記羽口から吹込む装置と、粗粒ダストを炉内へ装入する装置とを備えたことを特徴とするものである。
細粒ダストと粗粒ダストに分級する分級装置の分級区分は、粗粒ダストを廃棄物溶融炉の炉頂または炉側部からそのまま投入しても容易に炉外へ飛散しないような粒径以上とするように分級することが好ましい。すなわち、廃棄物溶融炉上部の炉内ガス流れに対して十分沈降できる粒径以上のダストを粗粒ダストとするように分級区分を定めるのが好ましい。分級区分として例えば5〜10mm程度とすると、粗粒ダストを炉頂または炉側部からそのまま投入しても容易に炉外へ飛散しないので好ましい。
分級装置として篩装置、気流分離装置、サイクロン、遠心分離装置などを用いることが好ましい。
(1) In the waste melting furnace according to the present invention, a high-temperature combustion zone is formed in the lower part of the furnace, and a waste layer is formed above the high-temperature combustion zone. A waste melting furnace that blows oxygen-containing gas into the high-temperature combustion zone, and receives dust collected from the waste melting furnace to collect fine dust and coarse particles. It comprises a classification device for classifying into dust, a device for blowing fine dust from the tuyere, and a device for charging coarse dust into the furnace.
The classification of the classifier that classifies fine dust and coarse dust is larger than the particle size so that even if coarse dust is thrown directly from the top or side of the waste melting furnace, it is not easily scattered outside the furnace. It is preferable to classify so that That is, it is preferable to determine the classification so that dust having a particle size or larger that can sufficiently settle with respect to the gas flow in the furnace at the upper part of the waste melting furnace is used as coarse dust. For example, when the classification is about 5 to 10 mm, it is preferable that coarse dust is not easily scattered outside the furnace even if it is directly supplied from the top or side of the furnace.
As a classification device, it is preferable to use a sieve device, an airflow separation device, a cyclone, a centrifugal separation device or the like.

(2)また、上記(1)に記載のものにおいて、廃棄物溶融炉に接続された二次燃焼炉、ボイラ、サイクロン及び減温装置のうち少なくとも一つから落下灰を回収して分級装置に供給する装置を備えたことを特徴とするものである。 (2) Further, in the above (1), the fall ash is recovered from at least one of a secondary combustion furnace, a boiler, a cyclone, and a temperature reducing device connected to the waste melting furnace, and is used as a classification device. It is characterized by having a supply device.

(3)また、本発明に係る廃棄物溶融炉の操業方法は、炉下部に高温燃焼帯が形成されて該高温燃焼帯の上方に廃棄物層が形成され、前記高温燃焼帯に酸素含有ガスを吹き込む羽口を有し、投入された廃棄物を熱分解すると共に残渣を溶融する廃棄物溶融炉の操業方法であって、前記廃棄物溶融炉から排出されたダストを回収するダスト回収工程と、該ダスト回収工程で回収されたダストを細粒ダストと粗粒ダストに分級する分級工程を有し、細粒ダストを前記羽口から吹込み、粗粒ダストを炉内へ装入することを特徴とするものである。 (3) Further, in the method of operating a waste melting furnace according to the present invention, a high-temperature combustion zone is formed in the lower part of the furnace, a waste layer is formed above the high-temperature combustion zone, and an oxygen-containing gas is formed in the high-temperature combustion zone. A waste melting furnace for thermally decomposing input waste and melting the residue, and a dust recovery step for recovering dust discharged from the waste melting furnace; , Having a classification step of classifying the dust recovered in the dust recovery step into fine dust and coarse dust, blowing fine dust from the tuyere, and charging the coarse dust into the furnace It is a feature.

(4)また、上記(3)に記載のものにおいて、ダスト回収工程は、廃棄物溶融炉に接続された二次燃焼炉、ボイラ、サイクロン及び減温装置のうち少なくとも一つから落下灰を回収する工程を含むことを特徴とするものである。 (4) In the above (3), the dust recovery step recovers the fallen ash from at least one of the secondary combustion furnace, boiler, cyclone, and temperature reducing device connected to the waste melting furnace. Including the step of performing.

本発明においては、廃棄物溶融炉から排出されて回収されたダストの供給を受けて該ダストを細粒ダストと粗粒ダストに分級する分級装置と、細粒ダストを前記羽口から吹込む手段と、粗粒ダストを炉内へ装入する手段とを備えたので、ダストによって羽口を閉塞させたり、炉内状況を悪化させたりすることなく、羽口から吹き込み溶融処理することができる。   In the present invention, a classifier that receives supply of dust discharged from a waste melting furnace and collects the dust into fine dust and coarse dust, and means for blowing fine dust from the tuyere And means for charging coarse dust into the furnace, so that the tuyere can be blown and melted from the tuyere without clogging the tuyere with the dust or deteriorating the condition in the furnace.

図1は本発明の一実施の形態に係る廃棄物ガス化溶融炉の説明図である。
ガス化溶融炉1は、前述したように、炉底部にコークスを堆積させ、このコークスの層に酸素富化空気を吹き込んで燃焼させることにより高温燃焼帯を形成し、この高温燃焼帯の上へ廃棄物を投入して熱分解させ残渣を溶融させるようになっている。
FIG. 1 is an explanatory diagram of a waste gasification melting furnace according to an embodiment of the present invention.
As described above, the gasification melting furnace 1 deposits coke at the bottom of the furnace, blows oxygen-enriched air into the coke layer, and burns it to form a high-temperature combustion zone. Waste is introduced and thermally decomposed to melt the residue.

このようなガス化溶融炉1は、以下のような構造になっている。
全体形状は、竪型で円筒形状に形成され、上部が拡径された形状になっている。この上部の拡径された部分はフリーボード部3である。そして、炉の上端部には廃棄物装入口5が設けられ、該廃棄物装入口5の近傍には、コークス、溶融スラグ性状調整剤である石灰石を装入口へ搬送する副資材搬送コンベア7が設置されている。
炉の上端部近くにはガス出口9が設けられ、炉の下部には溶融スラグ排出口11が設けられている。
Such a gasification melting furnace 1 has the following structure.
The overall shape is a bowl-shaped and cylindrical shape, with the upper part being expanded in diameter. The upper diameter-enlarged portion is a free board portion 3. A waste material inlet 5 is provided at the upper end of the furnace, and in the vicinity of the waste material inlet 5 there is a secondary material conveyor 7 that conveys coke and molten slag property modifier limestone to the inlet. is set up.
A gas outlet 9 is provided near the upper end of the furnace, and a molten slag outlet 11 is provided at the lower part of the furnace.

炉下部の高温燃焼帯が形成される位置にはコークスを燃焼させる空気又は酸素富化空気を吹込むための主羽口13が設けられている。主羽口13には送風配管15が接続され、送風配管15には主羽口13へ空気又は酸素富化空気を送風する送風機17が接続されている。
高温燃焼帯の上に存在する廃棄物の位置には投入された廃棄物を流動化させる空気を吹込むための副羽口19が設けられている。また、フリーボード部3には炉下部で生成した熱分解ガス(可燃性ガス)を部分燃焼させる空気を吹き込むための三段羽口21が設けられている。
A main tuyere 13 for blowing air for burning coke or oxygen-enriched air is provided at a position where a high-temperature combustion zone is formed in the lower part of the furnace. A blower pipe 15 is connected to the main tuyere, and a blower 17 that blows air or oxygen-enriched air to the main tuyere 13 is connected to the blower pipe 15.
A sub tuyere 19 is provided at the position of the waste existing above the high-temperature combustion zone for blowing air for fluidizing the input waste. The freeboard unit 3 is provided with a three-stage tuyere 21 for blowing air for partially combusting pyrolysis gas (combustible gas) generated in the lower part of the furnace.

ガス出口9の下流側にはガス化溶融炉1から排出された可燃性ガスを燃焼させる二次燃焼炉23が設置され、二次燃焼炉23の下流側には熱回収装置であるボイラ25が設置されている。さらに、ボイラ25の下流側には、同じく熱回収装置であるエコノマイザ27が設置され、エコノマイザ27の下流側には、排ガス中の比較的粗いダストを除去するサイクロン28が設置され、その下流側には熱回収された排ガスを排ガスの浄化処理に適する温度まで冷却するためのガス冷却器である減温塔29が設置されている。また、減温塔29の下流側にはバグフィルタ31が設置されている。   A secondary combustion furnace 23 for burning the combustible gas discharged from the gasification melting furnace 1 is installed on the downstream side of the gas outlet 9, and a boiler 25, which is a heat recovery device, is installed on the downstream side of the secondary combustion furnace 23. is set up. Further, an economizer 27, which is also a heat recovery device, is installed on the downstream side of the boiler 25, and a cyclone 28 for removing relatively coarse dust in the exhaust gas is installed on the downstream side of the economizer 27. Is provided with a temperature-decreasing tower 29 which is a gas cooler for cooling the heat-recovered exhaust gas to a temperature suitable for exhaust gas purification treatment. Further, a bag filter 31 is installed on the downstream side of the temperature reducing tower 29.

二次燃焼炉23、ボイラ25、エコノマイザ27、サイクロン28、及び減温塔29ではガス化溶融炉からの排ガス中の粗いダストが落下し落下灰としてそれぞれ抜き出される。そして、各装置から抜き出された落下灰を集め搬送するための落下灰搬送コンベア33が設置されている。
また、落下灰搬送コンベア33から落下灰の供給を受け、細粒灰と粗粒灰に分級する分級装置としての篩装置35が設けられている。なお、落下灰搬送コンベア33と篩装置35との間は搬送コンベアによって接続されているが、この搬送コンベアは図示を省略している。
In the secondary combustion furnace 23, the boiler 25, the economizer 27, the cyclone 28, and the temperature reducing tower 29, coarse dust in the exhaust gas from the gasification melting furnace falls and is extracted as fall ash. And the fall ash conveyance conveyor 33 for collecting and conveying the fall ash extracted from each apparatus is installed.
Further, a sieving device 35 is provided as a classification device that receives the supply of the falling ash from the falling ash conveyor 33 and classifies the ash into fine ash and coarse ash. In addition, although the fall ash conveyance conveyor 33 and the sieve apparatus 35 are connected by the conveyance conveyor, this conveyance conveyor is abbreviate | omitting illustration.

篩装置35の下方には、篩装置35で篩われた細粒灰を貯留する細粒灰貯留槽37が設けられている。細粒灰貯留槽37には、細粒灰貯留槽37から細粒灰を切り出すロータリーバルブ39が設けられ、切り出された細粒灰はシュート41、ゲート弁43を介して主羽口13に酸素含有ガスを供給する送風配管15に供給される。
篩装置35から篩上の粗粒灰を受けてガス化溶融炉の炉頂に設けられた装入口に搬送する粗粒灰搬送コンベア45が設けられている。
Below the sieving device 35, a fine ash storage tank 37 for storing fine ash sieved by the sieving device 35 is provided. The fine-grained ash storage tank 37 is provided with a rotary valve 39 for cutting out the fine-grained ash from the fine-grained ash storage tank 37, and the cut-out fine ash is oxygenated to the main tuyere 13 via the chute 41 and the gate valve 43. It is supplied to the blower pipe 15 for supplying the contained gas.
A coarse ash conveying conveyor 45 is provided that receives the coarse ash on the sieve from the sieving device 35 and conveys the coarse ash on the top of the gasification melting furnace.

上記のように構成された廃棄物ガス化溶融炉における廃棄物のガス化溶融処理は次のように行なわれる。
都市ごみや産業廃棄物或いは廃棄物焼却残渣などの廃棄物と、コークスと、石灰石とがそれぞれ計量され、ガス化溶融炉1内へ投入される。ガス化溶融炉1へ投入されたもののうち、コークスは炉底部に堆積し、ここに主羽口13から空気又は酸素富化空気(以下酸素含有ガスという)が吹き込まれる。
この酸素含有ガスの吹き込みによりコークスが燃焼し、高温燃焼帯が形成される。投入された廃棄物は高温燃焼帯の上方で、副羽口19から吹き込まれる空気によって流動しながら滞留して流動化層を形成する。廃棄物は流動化している間に予熱され、熱分解して可燃性ガスを発生する。
The waste gasification and melting treatment in the waste gasification and melting furnace configured as described above is performed as follows.
Waste such as municipal waste, industrial waste or waste incineration residue, coke and limestone are weighed and put into the gasification melting furnace 1. Among the components charged into the gasification melting furnace 1, coke is deposited at the bottom of the furnace, and air or oxygen-enriched air (hereinafter referred to as oxygen-containing gas) is blown into the main tuyere 13.
Coke is combusted by blowing the oxygen-containing gas, and a high-temperature combustion zone is formed. The thrown-in waste stays in the upper part of the high-temperature combustion zone while flowing by the air blown from the sub tuyere 19 to form a fluidized layer. Waste is preheated while it is fluidized and is pyrolyzed to generate flammable gases.

廃棄物の熱分解残渣は高温燃焼帯で溶融され、炉底部の溶融スラグ排出口11から抜き出される。
一方、廃棄物の熱分解により生成した可燃性ガスは、フリーボード部3において、三段羽口21から空気が吹込まれて部分燃焼し、ガス出口9から排出される。
ガス出口9から排出されたガスは、二次燃焼炉23で二次燃焼用空気が吹き込まれて燃焼した後、ボイラ25及びエコノマイザ27へ送られて熱回収される。熱回収された排ガスはサイクロン28で排ガス中の比較的粗いダストが除去され、さらに減温塔29で水が噴霧されて200℃以下程度に冷却される。
次いで、排ガス中へ、塩化水素を除去するための消石灰粉やダイオキシン類を吸着して除去するための活性炭などの有害物除去剤が吹き込まれ、バグフィルタ31へ送られて集塵処理される。バグフィルタ31で集塵された集塵灰は飛灰処理装置に送られて重金属類溶出防止処理を施されて埋立処分される。
The thermal decomposition residue of the waste is melted in the high temperature combustion zone and extracted from the molten slag discharge port 11 at the bottom of the furnace.
On the other hand, the combustible gas generated by the thermal decomposition of the waste is partly combusted when air is blown from the three-stage tuyere 21 in the free board portion 3 and is discharged from the gas outlet 9.
The gas discharged from the gas outlet 9 is blown into the secondary combustion air in the secondary combustion furnace 23 and burned, and then sent to the boiler 25 and the economizer 27 for heat recovery. The heat-recovered exhaust gas is subjected to cyclone 28 to remove relatively coarse dust in the exhaust gas, and further sprayed with water in a temperature reducing tower 29 to be cooled to about 200 ° C. or less.
Next, harmful substance removing agents such as activated carbon for adsorbing and removing slaked lime powder and dioxins for removing hydrogen chloride are blown into the exhaust gas, and sent to the bag filter 31 for dust collection. The dust collection ash collected by the bag filter 31 is sent to a fly ash treatment apparatus, subjected to heavy metal elution prevention treatment, and disposed of in landfill.

ガス化溶融炉1から排出されたガスがバグフィルタ31へ到達するまでの間に、落下灰が落下するので、二次燃焼炉23、ボイラ25、エコノマイザ27、サイクロン28、及び減温塔29から落下灰を抜き出し、落下灰搬送コンベア33に集めて搬送する。落下灰搬送コンベア33から篩装置35に、図示しない搬送コンベアで落下灰を搬送し、篩分ける。
そして、篩上の粗粒灰を粗粒灰搬送コンベア45により搬送し、炉頂から粗粒灰をそのままガス化溶融炉1内に投入して、廃棄物の熱分解残渣とともに溶融させスラグ化させる。粗粒灰は炉頂からそのまま投入しても粒径が比較的大きいので炉外へ飛散することが少なく、溶融処理される。
Since the fall ash falls before the gas discharged from the gasification melting furnace 1 reaches the bag filter 31, the secondary combustion furnace 23, the boiler 25, the economizer 27, the cyclone 28, and the temperature reducing tower 29 Dropped ash is extracted and collected and transported to the fallen ash transport conveyor 33. Dropped ash is transported from the falling ash transport conveyor 33 to the sieving device 35 by a transport conveyor (not shown) and sieved.
Then, the coarse ash on the sieve is conveyed by the coarse ash conveying conveyor 45, and the coarse ash is put into the gasification melting furnace 1 as it is from the top of the furnace, and is melted together with the pyrolysis residue of the waste to form slag. . Coarse ash has a relatively large particle size even if it is fed directly from the top of the furnace, so it hardly scatters outside the furnace and is melt-processed.

篩下の細粒灰は、細粒灰貯留槽37に貯留し、ロータリーバルブ39により所定量を切り出して、シュート41とゲート弁43を介して送風配管15内に供給し、主羽口13から高温燃焼帯へ吹き込む。細粒灰が主羽口から高温燃焼帯へ吹き込まれると、細粒灰は主羽口先の燃焼空間(レースウェイ)を通過する間に短時間で加熱溶融され、炉底部へ流下し熱分解残渣の溶融物とともに排出口11から抜き出される。   Fine ash under the sieve is stored in the fine ash storage tank 37, a predetermined amount is cut out by the rotary valve 39, supplied into the blower pipe 15 through the chute 41 and the gate valve 43, and from the main tuyere 13. Blow into the hot combustion zone. When fine ash is blown from the main tuyere into the high-temperature combustion zone, the fine ash is heated and melted in a short time while passing through the combustion space (raceway) at the tip of the main tuyere, and flows down to the bottom of the furnace, resulting in pyrolysis residue. Together with the molten material.

上記のように、落下灰を篩装置35により粗粒灰と細粒灰に分離し、細粒灰のみを主羽口から吹き込むようにしたので、落下灰によって主羽口の閉塞が生ずることがなく、また主羽口先で溶融不良が生じて炉内状況が悪化するのを防ぐことができる。また、粗粒灰も炉頂からそのまま投入し溶融処理するようにしたので、落下灰全量を溶融処理してスラグ化することができ、埋立処分量を削減することができる。   As described above, the fall ash is separated into the coarse ash and the fine ash by the sieving device 35, and only the fine ash is blown from the main tuyere, so that the main tuyere may be blocked by the fall ash. In addition, it is possible to prevent a melting failure from occurring at the main tuyere and aggravation of the furnace condition. Further, since the coarse ash is also charged from the top of the furnace and melted, the total amount of fallen ash can be melted to form slag, and the amount of landfill disposal can be reduced.

篩装置35の篩目は、篩上の粗粒灰を炉頂からそのまま投入しても容易に炉外へ飛散しないような粒径以上とするように篩分けする篩目が好ましい。すなわち、ガス化溶融炉上部の炉内ガス流れに対して十分沈降できる粒径以上のダストを篩上とするように篩目を定めるのが好ましい。篩装置35の篩目として例えば5〜10mm程度の篩目とすると、篩上の粗粒灰を炉頂からそのまま投入しても容易に炉外へ飛散しないので好ましい。
また、篩装置35の形式は問わないが、振動篩を用いるのが好ましい。
The sieve of the sieving device 35 is preferably a sieve that is sieved so that the coarse ash on the sieve is not larger than the particle size so that it does not easily scatter out of the furnace even if it is fed directly from the top of the furnace. That is, it is preferable to determine the sieve so that dust having a particle size or larger that can sufficiently settle with respect to the gas flow in the furnace at the upper part of the gasification melting furnace is used as the sieve. For example, a sieve having a size of about 5 to 10 mm is preferred as the sieve of the sieving device 35, since the coarse ash on the sieve is not easily scattered from the furnace top even if it is directly fed from the furnace top.
Moreover, although the format of the sieving device 35 is not ask | required, it is preferable to use a vibration sieve.

なお、バグフィルタ31で捕集された集塵灰の一部を篩装置35に搬送し、落下灰とともに溶融処理するようにしてもよい。
集塵灰の一部を溶融処理することにより集塵灰に含まれる重金属類は溶融処理されて生成したスラグ中に不溶出な形態で含有される。そのため、重金属類溶出防止処理を施し埋立処分する集塵灰量を削減できる。
なお、バグフィルタで回収された集塵灰の20〜25%を溶融処理するようにすることが、上記のプロセスにそって操業するのに好ましい。
A part of the collected ash collected by the bag filter 31 may be conveyed to the sieving device 35 and melted together with the falling ash.
The heavy metals contained in the dust collection ash by melting a part of the dust collection ash are contained in a non-eluting form in the slag produced by the melt treatment. Therefore, it is possible to reduce the amount of dust collection ash that is subjected to heavy metal elution prevention treatment and landfilled.
In addition, it is preferable to operate according to said process to melt-process 20-25% of the dust collection ash collect | recovered with the bag filter.

また、落下灰を細粒灰と粗粒灰に分級する分級装置としては、篩装置に限らず気流分離装置、サイクロン、遠心分離装置など他の分級装置を用いることができる。気流分離装置では所定の流速の気流により、落下灰を気流に搬送される細粒灰と、搬送されずに沈降する粗粒灰とに分級する。細粒灰をバグフィルタなどで集塵して細粒灰貯留槽37に貯留し、粗粒灰を炉内へ装入するようにする。ガス化溶融炉の炉内ガス流速と同程度かそれ以上の流速の気流により分級することにより、粗粒灰を炉頂からそのまま投入してもガス化溶融炉上部の炉内ガス流れに対して十分沈降でき、容易に炉外へ飛散しないような粒径以上の落下灰を粗粒灰とするように分級することができる。
サイクロンでは粗粒灰が沈降して分離され分級される。
Moreover, as a classification apparatus which classifies fall ash into a fine ash and a coarse ash, not only a sieve apparatus but other classification apparatuses, such as an airflow separator, a cyclone, and a centrifugal separator, can be used. In the airflow separation device, the fall ash is classified into fine ash that is transported into the airflow and coarse ash that settles without being transported by the airflow at a predetermined flow velocity. Fine ash is collected by a bag filter or the like and stored in the fine ash storage tank 37 so that the coarse ash is charged into the furnace. Even if the coarse ash is charged as it is from the top of the furnace by classifying it with an air flow at the same or higher flow rate than the gas flow rate in the gasification melting furnace, Falling ash having a particle size that can settle sufficiently and does not easily fly out of the furnace can be classified so as to be coarse ash.
In the cyclone, coarse ash settles and is separated and classified.

また、粗粒灰をガス化溶融炉の炉頂から装入する以外に、炉側部に装入口を設けて装入してもよいし、両方から装入してもよい。また、廃棄物を貯留する廃棄物ピットに粗粒灰を搬送し、廃棄物とともにガス化溶融炉に装入してもよい。   Moreover, in addition to charging coarse ash from the top of the gasification melting furnace, it may be charged by providing a charging port on the side of the furnace, or may be charged from both. Alternatively, coarse ash may be transported to a waste pit for storing waste and charged into a gasification melting furnace together with the waste.

本発明の一実施の形態に係る廃棄物ガス化溶融炉の説明図である。It is explanatory drawing of the waste gasification melting furnace which concerns on one embodiment of this invention.

符号の説明Explanation of symbols

1 ガス化溶融炉
5 廃棄物装入口
9 ガス出口
13 主羽口
23 二次燃焼炉
25 ボイラ
29 減温塔
33 落下灰搬送コンベア
35 篩装置
37 細粒灰貯留槽
45 粗粒灰搬送コンベア
DESCRIPTION OF SYMBOLS 1 Gasification melting furnace 5 Waste inlet 9 Gas outlet 13 Main tuyere 23 Secondary combustion furnace 25 Boiler 29 Temperature-reducing tower 33 Falling ash conveyance conveyor 35 Sieve apparatus 37 Fine grain ash storage tank 45 Coarse ash conveyance conveyor

Claims (4)

炉下部に高温燃焼帯が形成されて該高温燃焼帯の上方に廃棄物層が形成され、投入された廃棄物を熱分解すると共に残渣を溶融する廃棄物溶融炉であって、
前記高温燃焼帯に酸素含有ガスを吹き込む羽口と、前記廃棄物溶融炉から排出されて回収されたダストの供給を受けて該ダストを細粒ダストと粗粒ダストに分級する分級装置と、細粒ダストを前記羽口から吹込む装置と、粗粒ダストを炉内へ装入する装置とを備えたことを特徴とする廃棄物溶融炉。
A waste melting furnace in which a high-temperature combustion zone is formed at the bottom of the furnace and a waste layer is formed above the high-temperature combustion zone, and the waste that has been charged is thermally decomposed and the residue is melted,
A tuyere that blows oxygen-containing gas into the high-temperature combustion zone, a classification device that receives the supply of dust discharged from the waste melting furnace and recovered, and classifies the dust into fine dust and coarse dust; A waste melting furnace comprising a device for blowing granular dust from the tuyere and a device for charging coarse dust into the furnace.
廃棄物溶融炉に接続された二次燃焼炉、ボイラ、サイクロン及び減温装置のうち少なくとも一つから落下灰を回収して分級装置に供給する装置を備えたことを特徴とする請求項1に記載の廃棄物溶融炉。 The apparatus according to claim 1, further comprising a device that collects the fall ash from at least one of a secondary combustion furnace, a boiler, a cyclone, and a temperature reduction device connected to the waste melting furnace and supplies the ash to a classification device. The waste melting furnace described. 炉下部に高温燃焼帯が形成されて該高温燃焼帯の上方に廃棄物層が形成され、前記高温燃焼帯に酸素含有ガスを吹き込む羽口を有し、投入された廃棄物を熱分解すると共に残渣を溶融する廃棄物溶融炉の操業方法であって、
前記廃棄物溶融炉から排出されたダストを回収するダスト回収工程と、該ダスト回収工程で回収されたダストを細粒ダストと粗粒ダストに分級する分級工程を有し、細粒ダストを前記羽口から吹込み、粗粒ダストを炉内へ装入することを特徴とする廃棄物溶融炉の操業方法。
A high-temperature combustion zone is formed in the lower part of the furnace, a waste layer is formed above the high-temperature combustion zone, and there is a tuyere that blows oxygen-containing gas into the high-temperature combustion zone. A method of operating a waste melting furnace for melting residues,
A dust recovery step for recovering dust discharged from the waste melting furnace, and a classification step for classifying the dust recovered in the dust recovery step into fine dust and coarse dust, A method of operating a waste melting furnace, characterized by blowing from the mouth and charging coarse dust into the furnace.
ダスト回収工程は、廃棄物溶融炉に接続された二次燃焼炉、ボイラ、サイクロン及び減温装置のうち少なくとも一つから落下灰を回収する工程を含むことを特徴とする請求項3に記載の廃棄物溶融炉の操業方法。 The dust recovery step includes a step of recovering fall ash from at least one of a secondary combustion furnace, a boiler, a cyclone, and a temperature reducing device connected to the waste melting furnace. Waste melting furnace operation method.
JP2006259900A 2006-09-26 2006-09-26 Waste melting furnace and waste melting furnace operating method Expired - Fee Related JP4918833B2 (en)

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* Cited by examiner, † Cited by third party
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JP2010151420A (en) * 2008-12-26 2010-07-08 Nippon Steel Engineering Co Ltd Method of enhancing capacity of waste disposal equipment
CN110669921A (en) * 2019-10-18 2020-01-10 甘肃酒钢集团宏兴钢铁股份有限公司 System and method for resourcefully treating steelmaking secondary dedusting ash

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JP2001041429A (en) * 1999-08-02 2001-02-13 Nippon Steel Corp Method for treating used carbon based adsorbent
JP2001108209A (en) * 1999-10-04 2001-04-20 Nippon Steel Corp Combustible dust blowing facility for waste melting furnace

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Publication number Priority date Publication date Assignee Title
JP2001041429A (en) * 1999-08-02 2001-02-13 Nippon Steel Corp Method for treating used carbon based adsorbent
JP2001108209A (en) * 1999-10-04 2001-04-20 Nippon Steel Corp Combustible dust blowing facility for waste melting furnace

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2008272707A (en) * 2007-05-07 2008-11-13 Takuma Co Ltd Method for suppressing elution of hexavalent chromium from incineration fly ash of fuel containing chromium and combustion apparatus to be used therefor
JP2010151420A (en) * 2008-12-26 2010-07-08 Nippon Steel Engineering Co Ltd Method of enhancing capacity of waste disposal equipment
CN110669921A (en) * 2019-10-18 2020-01-10 甘肃酒钢集团宏兴钢铁股份有限公司 System and method for resourcefully treating steelmaking secondary dedusting ash
CN110669921B (en) * 2019-10-18 2023-10-27 甘肃酒钢集团宏兴钢铁股份有限公司 System and method for recycling steelmaking secondary dust removal ash

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