JPH05133515A - Method for drying incinerated ash and melting treatment process therefor - Google Patents
Method for drying incinerated ash and melting treatment process thereforInfo
- Publication number
- JPH05133515A JPH05133515A JP32704891A JP32704891A JPH05133515A JP H05133515 A JPH05133515 A JP H05133515A JP 32704891 A JP32704891 A JP 32704891A JP 32704891 A JP32704891 A JP 32704891A JP H05133515 A JPH05133515 A JP H05133515A
- Authority
- JP
- Japan
- Prior art keywords
- ash
- incinerator
- stoker
- combustion
- post
- 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
Links
Landscapes
- Gasification And Melting Of Waste (AREA)
Abstract
Description
【0001】[0001]
【産業上の利用分野】本発明は、湿気を帯びた焼却灰の
乾燥方法とその溶融処理方法の改良に関するものであ
り、主としてストーカ式焼却炉に付設した灰の溶融処理
プラントに於いて利用されるものである。BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a method for drying incinerated ash having moisture and an improvement in its melting treatment method, and is mainly used in an ash melting treatment plant attached to a stoker incinerator. It is something.
【0002】[0002]
【従来の技術】一般に、都市ごみや下水汚泥、産業廃棄
物等の焼却炉から排出される燃焼残渣は、その多くが埋
立により処理されている。しかし、近年埋め立て地が逼
迫してその確保が年々困難になりつつあり、これに伴っ
て燃焼残渣の減容化に対する要望が増々高まっている。
また、燃焼残渣を埋立処理した場合には、重金属等の溶
出による環境汚染を生じる虞れがあるため、環境保全に
対する要望も高まりつつある。2. Description of the Related Art Generally, most of the combustion residues discharged from incinerators such as municipal waste, sewage sludge and industrial waste are treated by landfill. However, in recent years, landfills have become tight and it is becoming more difficult to secure them year by year, and along with this, there is an increasing demand for volume reduction of combustion residues.
Further, when the combustion residue is landfilled, there is a risk of environmental pollution due to elution of heavy metals and the like, and therefore there is an increasing demand for environmental protection.
【0003】一方、上述の如き要望に対応するため、近
年所謂焼却灰の溶融処理方法が開発され、実用に供され
ている。焼却灰を溶融することにより、減容化や重金属
の溶出防止が可能となり、また灰を資源として再活用で
きるからである。ところで、灰の溶融炉には、燃料バー
ナで焼却灰を表面から加熱溶融するバーナ溶融方式の炉
と、アーク熱又はジュール熱で焼却灰を加熱溶融する電
気溶融方式の炉とが現存するが、何れの方式の炉にあっ
ても、焼却灰の溶融効率を高めると云う点から、炉内へ
投入する焼却灰の水分は少ない方が好都合である。On the other hand, in order to meet the above demands, a so-called incineration ash melting treatment method has been developed and put into practical use in recent years. This is because by melting the incinerated ash, it is possible to reduce the volume and prevent the elution of heavy metals, and the ash can be reused as a resource. By the way, in the ash melting furnace, a burner melting type furnace that heats and melts the incineration ash from the surface with a fuel burner, and an electric melting type furnace that heats and melts the incineration ash by arc heat or Joule heat exist, Regardless of which type of furnace is used, it is advantageous that the water content of the incinerated ash to be fed into the furnace is low, since the melting efficiency of the incinerated ash is increased.
【0004】そのため、ごみや汚泥等の焼却炉の建設と
同時期に灰溶融炉を併設する場合には、通常図5に示す
ように、焼却灰を水で消火した湿灰の形式で焼却炉より
取り出さず、自然冷却により消火せしめた乾灰の形式で
焼却炉より取り出す方式が採用される。即ち、図5に示
す如く、焼却炉1の灰出しシュート5からガスシールダ
ンパー6を通して排出された燃焼残渣Bは、自然冷却に
より消火される。その後、冷却された乾燥灰Cは、乾灰
移送コンベア9により破砕機16へ送られ、灰中のクリ
ンカー等の夾雑物が破砕される。破砕された乾燥灰C
は、引き続き乾灰振動スクリーン8、乾灰振動コンベア
10、磁選機11等を経て微粒乾燥灰Cと鉄分Dに分別
され、分別された乾燥灰Cは、コンベア12により焼却
炉1に併設した灰溶融炉13内へ順次供給されて行く。Therefore, when an ash melting furnace is installed at the same time as the construction of an incinerator for refuse, sludge, etc., the incinerator is usually in the form of wet ash extinguished with water as shown in FIG. Instead of taking it out further, a method of taking it out from the incinerator in the form of dry ash extinguished by natural cooling is adopted. That is, as shown in FIG. 5, the combustion residue B discharged from the ash discharge chute 5 of the incinerator 1 through the gas seal damper 6 is extinguished by natural cooling. Then, the cooled dry ash C is sent to the crusher 16 by the dry ash transfer conveyor 9, and foreign substances such as clinker in the ash are crushed. Crushed dry ash C
Is continuously separated into fine dry ash C and iron D through a dry ash vibrating screen 8, a dry ash vibrating conveyor 10, a magnetic separator 11 and the like, and the separated dry ash C is attached to the incinerator 1 by a conveyor 12. It is sequentially supplied into the melting furnace 13.
【0005】一方、図6に示す如く、所謂フライトコン
ベア31により水中で燃焼残渣Bを冷却して消火し、所
謂湿った焼却灰(湿灰)Aを取り出しているごみ焼却炉
に於いては、焼却灰Aの溶融処理に際して焼却灰Aを乾
燥せしめる必要がある。そのため、一般には分別した焼
却灰(湿灰)Aをロータリーキルン型乾燥機32へ送り
込み、灰溶融炉13から抜き出した排ガスEを熱源とし
て焼却灰Aを乾燥させ、乾燥せしめた乾燥灰Cをコンベ
ア12により灰溶融炉13内へ供給するようにしてい
る。乾燥後の排ガスEは、焼却炉1に導びかれる。尚、
図6に於いて7は助燃装置、E1は灰溶融炉13からの
排ガスである。On the other hand, as shown in FIG. 6, in a refuse incinerator in which a combustion residue B is cooled in water by a so-called flight conveyor 31 to extinguish the fire and a so-called wet incineration ash (wet ash) A is taken out, It is necessary to dry the incineration ash A in the melting process of the incineration ash A. Therefore, generally, the separated incinerated ash (wet ash) A is sent to the rotary kiln type dryer 32, the incinerated ash A is dried by using the exhaust gas E extracted from the ash melting furnace 13 as a heat source, and the dried ash C that has been dried is conveyed 12 Is supplied into the ash melting furnace 13. The exhaust gas E after drying is guided to the incinerator 1. still,
In FIG. 6, 7 is an auxiliary combustion device, and E 1 is an exhaust gas from the ash melting furnace 13.
【0006】[0006]
【発明が解決しようとする課題】而して、前記図6の灰
の乾燥・溶融システムに於いては、湿灰と乾灰とその中
間状態の灰を夫々搬送する必要があり、特に湿灰の場合
には、機器に付着した灰が乾燥固着して装置の連続運転
が阻害され易く、作業能率が極めて低いと云う問題があ
る。また、図6の灰の乾燥・溶融システムに於いては、
灰の分別装置の他に焼却灰(湿灰)Aを乾燥させるため
のロータリーキルン32を別途に必要とするため、設備
費や保守点検費が嵩み、灰の溶融処理費の引き下げが計
り難いと云う問題がある。Therefore, in the ash drying / melting system shown in FIG. 6, it is necessary to convey wet ash, dry ash and ash in an intermediate state between them, and particularly wet ash. In such a case, there is a problem that the ash adhering to the equipment is dried and adhered and the continuous operation of the equipment is easily obstructed, and the work efficiency is extremely low. In addition, in the ash drying / melting system of FIG.
In addition to the ash separation device, a rotary kiln 32 for drying incinerated ash (wet ash) A is additionally required, so equipment costs and maintenance and inspection costs increase, and it is difficult to reduce the ash melting processing cost. There is a problem to say.
【0007】これに対して、前記図5に示す灰の溶融シ
ステムでは、焼却炉1から乾燥灰Cを直接取り出すよう
にしているため、十分な防塵対策が必要とするものの、
灰分別装置等の連続運転が容易となり、且つロータリー
キルン32等の乾燥装置を必要とすることもない。しか
し乍ら、図5のような乾灰受入方式の溶融炉にあって
も、既設の他のごみ焼却炉等から排出された焼却灰(湿
灰)Aを受け入れて、これを同時に溶融処理しなければ
ならないケースが屡々起生する。この様なケースに対処
するためには、図5のシステムに更に図6と同様の焼却
灰(湿灰)Aの乾燥装置を別途に設ける必要があり、そ
の結果、前述と同様に設備費や運転費が高騰したり、溶
融炉の連続運転が阻害されて処理能率が低下する等の問
題を生ずることになる。On the other hand, in the ash melting system shown in FIG. 5, since the dry ash C is taken out directly from the incinerator 1, although sufficient dustproof measures are required,
Continuous operation of the ash fractionation device and the like becomes easy, and a drying device such as the rotary kiln 32 is not required. However, even in the dry ash receiving type melting furnace as shown in Fig. 5, the incinerator ash (wet ash) A discharged from another existing refuse incinerator or the like is received and simultaneously melted and processed. Cases that have to occur often occur. In order to deal with such a case, it is necessary to additionally install a drying device for incinerated ash (wet ash) A similar to that in FIG. 6 in the system of FIG. There are problems that the operating cost rises, the continuous operation of the melting furnace is disturbed, and the processing efficiency decreases.
【0008】本件発明は、従前の焼却灰の乾燥やその溶
融処理に於ける上述の如き問題の解決を課題とするもの
であり、ストーカ式焼却炉の後燃焼ストーカを利用して
湿った焼却灰Aを効率よく乾燥させることにより、ロー
タリーキルン等の乾燥装置を別途に設けることなしに前
記焼却灰Aを能率よく乾燥若しくは乾燥並びに溶融処理
できるようにした湿った焼却灰の乾燥方法とその溶融処
理方法を提供するものである。The present invention is intended to solve the above-described problems in the conventional drying of incineration ash and its melting treatment, and the incineration ash moistened by using a post-burning stoker in a stoker type incinerator. A method for drying wet incineration ash and a method for melting the same, by efficiently drying A, so that the incineration ash A can be efficiently dried or dried and melt-processed without separately providing a drying device such as a rotary kiln. Is provided.
【0009】[0009]
【課題を解決するための手段】本件請求項1に記載の発
明は、他の焼却炉等から排出され焼却灰(湿灰)Aをス
トーカ式焼却炉1の後燃焼ストーカ4上へ散布し、後燃
焼ストーカ4上の燃焼残渣Bと混合せしめて焼却灰Aを
乾燥せしめると共に、前記燃焼残渣Bと乾燥せしめた焼
却灰Aとを乾燥状態で焼却炉1外へ取り出すことを発明
の基本構成とするものである。According to the invention described in claim 1, the incineration ash (wet ash) A discharged from another incinerator or the like is sprayed on the post-combustion stoker 4 of the stoker type incinerator 1. The basic constitution of the invention is to dry the incineration ash A by mixing with the combustion residue B on the post-combustion stoker 4 and to take out the combustion residue B and the dried incineration ash A in the dry state to the outside of the incinerator 1. To do.
【0010】また、本件請求項4に記載の発明は、他の
焼却炉等から排出された焼却灰Aをストーカ式焼却炉1
の後燃焼ストーカ4上へ散布して焼却灰Aを乾燥せしめ
ると共に、後燃焼ストーカ4上の燃焼残渣Bと乾燥せし
めた焼却灰Aとを乾燥状態で焼却炉1外へ取り出し、更
に鉄分Dも除去したあとの乾燥灰Cを灰溶融炉13内へ
供給することを発明の基本構成とするものである。In the invention according to claim 4, the incinerator ash A discharged from another incinerator or the like is stoker-type incinerator 1
The incineration ash A is sprayed onto the post-combustion stoker 4 to dry it, and the combustion residue B on the post-combustion stoker 4 and the dried incineration ash A are taken out of the incinerator 1 in a dry state, and iron D is also included. The dry ash C after the removal is supplied to the ash melting furnace 13 as a basic constitution of the invention.
【0011】[0011]
【作用】ごみ等を燃焼中のストーカ式焼却炉1の後燃焼
ストーカ4上へ、炉側壁上方より湿った焼却灰Aを散布
することにより、焼却灰Aはストーカ4上の高温燃焼残
渣Bと混合されると共に、ストーカ4の下方から吹き込
まれた高温燃焼用空気に触れ、乾燥される。乾燥された
焼却灰Aは、ストーカ4上の燃焼残渣Bと一緒に炉外へ
乾燥状態で排出され、冷却されたのち乾燥灰Cとして灰
溶融炉13内へ供給されていく。[Operation] By spraying the moist incineration ash A from the upper side of the furnace side wall onto the post-combustion stoker 4 on which the stoker incinerator 1 is burning dust, the incineration ash A becomes a high temperature combustion residue B on the stoker 4. While being mixed, the high temperature combustion air blown from below the stoker 4 is touched and dried. The dried incinerated ash A is discharged to the outside of the furnace in a dry state together with the combustion residue B on the stoker 4, cooled, and then supplied as dry ash C into the ash melting furnace 13.
【0012】[0012]
【実施例】以下、図面に基づいて本発明の実施例を説明
する。図1は、本発明の実施に使用する湿った焼却灰の
乾燥・溶融プラントの構成説明図である。尚、図1に於
いて、従来例の図5及び図6と共通する部位には、これ
と同一の参照番号が使用されている。図に於いて、1は
ごみ等の焼却炉、2は乾燥ストーカ、3は燃焼ストー
カ、4は後燃焼ストーカ、5は灰出しシュート、6はガ
スシールダンパー、7は助燃バーナ、8は乾灰振動スク
リーン、9は乾灰移送コンベア、10は乾灰振動コンベ
ア、11は磁選機、12はコンベア、13は灰溶融炉、
14は金属バンカー、15はコンベア、16は破砕機、
17はコンベア、18は焼却灰ピット、19は灰供給ク
レーン、20は灰ホッパー、21は焼却灰供給プッシャ
ー、22は焼却灰振動スクリーン、23はコンベア、2
4はガスシールダンパー、25は焼却灰導入シュート、
26は灰分散装置、Aは湿った焼却灰、Bは燃焼残渣、
Cは乾燥灰、Dは鉄分である。Embodiments of the present invention will be described below with reference to the drawings. FIG. 1 is a structural explanatory view of a wet incineration ash drying / melting plant used for carrying out the present invention. In FIG. 1, the same reference numerals are used for the portions common to FIGS. 5 and 6 of the conventional example. In the figure, 1 is an incinerator for refuse and the like, 2 is a dry stoker, 3 is a combustion stoker, 4 is a post-combustion stoker, 5 is an ashing chute, 6 is a gas seal damper, 7 is an auxiliary burner, and 8 is dry ash. Vibrating screen, 9 dry ash transfer conveyor, 10 dry ash vibrating conveyor, 11 magnetic separator, 12 conveyor, 13 ash melting furnace,
14 is a metal bunker, 15 is a conveyor, 16 is a crusher,
17 is a conveyor, 18 is an incineration ash pit, 19 is an ash supply crane, 20 is an ash hopper, 21 is an incinerator ash supply pusher, 22 is an incinerator ash vibrating screen, 23 is a conveyor, 2
4 is a gas seal damper, 25 is an incineration ash introduction chute,
26 is an ash disperser, A is moist incineration ash, B is a combustion residue,
C is dry ash and D is iron.
【0013】前記灰分散装置26は図2及び図3に示す
如く、焼却炉1の後燃焼ストーカ4の側壁上部に穿設し
た焼却灰供給口1aの近傍に設けられている。即ち、当
該灰分散装置26は、回転自在に軸支した円筒体26a
とその外表面に固着した複数のリブ26b等から形成さ
れており、矢印方向へ一定速度で駆動装置(図示省略)
により回転されることにより、焼却灰Aを後燃焼ストー
カ4上へ均等に散布する。尚、本実施例では炉側壁上部
に焼却灰供給口1aを設けているが、炉の天井壁に供給
口1aを設け、灰を直接若しくは灰分散装置26を用い
て後燃焼ストーカ上へ分散するようにしてもよい。ま
た、本実施例では灰分散装置26として回転ドラム型の
装置を利用しているが、炉天井壁に供給口1aを設けた
ような場合には、ガイド板の上端部を揺動自在に軸支し
て、揺動するガイド板の上へ灰を落下させる型式の分散
装置26であってもよく、灰Aを有効に分散できるもの
であれば如何なる型式の装置であってもよい。As shown in FIGS. 2 and 3, the ash dispersion device 26 is provided in the vicinity of the incineration ash supply port 1a formed in the upper part of the side wall of the post combustion stoker 4 of the incinerator 1. That is, the ash disperser 26 includes a cylindrical body 26a that is rotatably supported.
And a plurality of ribs 26b fixed to the outer surface thereof and the like, and a driving device (not shown) at a constant speed in the arrow direction.
The incineration ash A is evenly scattered on the post-combustion stoker 4 by being rotated by. Although the incineration ash supply port 1a is provided in the upper part of the furnace side wall in this embodiment, the supply port 1a is provided in the furnace ceiling wall to disperse the ash directly or on the post-combustion stoker using the ash dispersion device 26. You may do it. Further, in the present embodiment, a rotary drum type device is used as the ash dispersion device 26, but in the case where the supply port 1a is provided on the furnace ceiling wall, the upper end of the guide plate is pivoted so that it can swing. It may be a dispersion device 26 of a type that supports the ash to drop it onto a swinging guide plate, or any type of device that can effectively disperse the ash A.
【0014】図4は焼却炉1のストーカ下部への燃焼用
空気の供給系統を示すものであり、押込通風機27を通
して常温空気S1が、また空気予熱器28を通して約2
50℃前後の高温空気S2が夫々乾燥ストーカ2、燃焼
ストーカ3及び後燃焼ストーカ4の下方から供給されて
いる。尚、29,30は風量調整用ダンパーである。FIG. 4 shows a system for supplying combustion air to the lower part of the stoker of the incinerator 1. Room temperature air S 1 is passed through the forced draft fan 27 and about 2 air is passed through the air preheater 28.
High-temperature air S 2 of about 50 ° C. is supplied from below the dry stoker 2, the combustion stoker 3, and the post-combustion stoker 4, respectively. In addition, 29 and 30 are dampers for adjusting the air flow.
【0015】次に、本発明による湿った焼却灰Aの乾燥
方法とその溶融処理方法について説明する。既設の都市
ごみや汚泥等の焼却炉1から排出された焼却灰(湿灰)
Aは、コンベアやトラック等で処理プラントへ搬入さ
れ、焼却灰ピット18内へ貯留される。貯留された焼却
灰Aは灰供給クレーン19により灰ホッパー20内へ投
入され、焼却灰供給プッシャー21の作動により焼却灰
振動スクリーン22上へ定量供給される。尚、選別され
たクリンカー等の大塊物は破砕機16で破砕されたあ
と、コンベア17を介して焼却灰ピット18へ戻され
る。Next, the method for drying the wet incinerated ash A and the method for melting the same according to the present invention will be described. Incinerated ash (wet ash) discharged from the incinerator 1 for existing municipal solid waste and sludge
A is carried into the processing plant by a conveyor, a truck, or the like, and stored in the incineration ash pit 18. The stored incinerated ash A is put into the ash hopper 20 by the ash supply crane 19 and is supplied in a fixed amount onto the incinerated ash vibrating screen 22 by the operation of the incinerated ash supply pusher 21. The selected large lumps such as clinker are crushed by the crusher 16 and then returned to the incineration ash pit 18 via the conveyor 17.
【0016】焼却灰振動スクリーン22からの細粒灰は
コンベア23、ガスシールダンパー24及び焼却灰導入
シュート25を通して灰分散装置26へ供給され、高速
回転をする円筒体26aの胴部に固設したリブ26bに
より、焼却灰供給口1aを通して後燃焼ストーカ4上へ
均等に散布される。即ち、散布された焼却灰Aは後燃焼
ストーカ4上の高温の燃焼残渣Bと混合されることによ
り、乾燥されることになる。また、焼却灰Aの乾燥用熱
量が不足する場合には、助燃バーナ7を作動して不足熱
量が補充される。Fine ash from the incineration ash vibrating screen 22 is supplied to an ash dispersion device 26 through a conveyor 23, a gas seal damper 24 and an incineration ash introduction chute 25, and is fixed to the body of a cylindrical body 26a rotating at high speed. The ribs 26b evenly spread the ash on the post-combustion stoker 4 through the incineration ash supply port 1a. That is, the scattered incineration ash A is dried by being mixed with the hot combustion residue B on the post-combustion stoker 4. When the amount of heat for drying the incinerated ash A is insufficient, the auxiliary burner 7 is operated to replenish the amount of insufficient heat.
【0017】尚、焼却炉1は乾燥、燃焼、後燃焼の過程
を経てごみ等を完全に燃焼するが、湿った焼却灰Aはご
みの燃焼過程に最も影響の少ない後燃焼ストーカ4上
へ、可能な限り均等な厚さに散布するのが望ましい。ま
た、後燃焼ストーカ4上へ散布された焼却灰Aは後燃焼
段階の高温燃焼残渣Bの上方へ乗りかかるため、後燃焼
中の火炎を消す虞れがある。そのため、湿った焼却灰A
を後燃焼ストーカ4上へ散布する場合には、後燃焼スト
ーカ4の下方より供給する燃焼用空気を高温状態に維持
し、高温空気(最高約250℃)による通気乾燥を行う
のが望ましい。即ち、風量調整ダンパー29を開及びダ
ンパー30を閉方向に制御し、後燃焼ストーカ4への燃
焼用空気を増加すると共にこれを高温化することによ
り、焼却灰Aの散布による火炎の消えを防止する。Although the incinerator 1 completely burns dust through the processes of drying, burning, and post-burning, the wet incinerator ash A is transferred to the post-burning stoker 4, which has the least influence on the burning process of dust, It is desirable to apply as evenly as possible the thickness. Further, since the incineration ash A scattered on the post-combustion stoker 4 rides above the high temperature combustion residue B in the post-combustion stage, there is a risk of extinguishing the flame during post-combustion. Therefore, damp incineration ash A
When sprayed on the post-combustion stoker 4, it is desirable to maintain the combustion air supplied from below the post-combustion stoker 4 in a high temperature state and perform aeration drying with high-temperature air (up to about 250 ° C.). That is, by controlling the air volume adjusting damper 29 to open and the damper 30 to close, increasing the combustion air to the post-combustion stoker 4 and raising the temperature thereof, the extinction of the flame due to the spraying of the incineration ash A is prevented. To do.
【0018】更に、前記焼却炉1の各ストーカ2,3,
4下方へ供給する燃焼用空気の温度や風量は、図4に示
す如く各ストーカ毎に任意に調整することが出来るた
め、前記上流側の乾燥ストーカ2及び燃焼ストーカ3へ
供給する燃焼用空気Sの温度及び風量をごみ質に合った
値に調整することにより、焼却灰Aの散布が行われて
も、両ストーカ2,3上のごみ等の燃焼は何等影響を受
けることなしに、良好な燃焼状態を継続することができ
る。Further, each of the stokers 2, 3, of the incinerator 1 is
4. The temperature and air volume of the combustion air supplied downward can be arbitrarily adjusted for each stoker as shown in FIG. 4, so that the combustion air S supplied to the upstream drying stoker 2 and the combustion stoker 3 can be adjusted. Even if the incineration ash A is sprayed by adjusting the temperature and air volume of the stoker to a value that suits the quality of the waste, the combustion of the waste on both stokers 2 and 3 will not be affected and will be good. The combustion state can be continued.
【0019】乾燥された焼却灰Aは、下層の燃焼残渣B
と一緒に灰出しシュート5を通して焼却炉1の外方へ乾
燥状態で取り出され、前記図5の場合と同様に乾灰振動
スクリーン8、乾灰移送コンベア9、乾灰振動コンベア
10及び磁選機11等を経て細粒乾燥灰Cが分別され
る。また、分別された乾燥灰Cはコンベア12により灰
溶融炉13へ供給され、ここで所謂灰の溶融処理が行わ
れる。The dried incineration ash A is the combustion residue B of the lower layer.
Along with the ash discharge chute 5, it is taken out of the incinerator 1 in a dry state, and as in the case of FIG. 5, the dry ash vibrating screen 8, the dry ash transfer conveyor 9, the dry ash vibrating conveyor 10 and the magnetic separator 11 are used. The fine-grained dry ash C is separated through the above. The separated dry ash C is supplied to the ash melting furnace 13 by the conveyor 12, and so-called ash melting processing is performed here.
【0020】[0020]
【発明の効果】本発明に於いては、ストーカ式焼却炉の
後燃焼ストーカ4を用いて湿った焼却灰Aを乾燥する構
成としているため、ロータリーキルン等の湿灰乾燥装置
やその付帯設備が全く不要となり、設備が簡素化される
と共に湿灰の固着等によるトラブルの発生が皆無とな
り、焼却灰の乾燥や乾燥・溶融処理の能率が大幅に向上
する。 また、焼却灰Aの乾燥の際に発生する水蒸気や
臭気等は、焼却炉1内の高温燃焼ガスと混合して脱臭さ
れると共に、ごみ焼却炉の排ガス処理装置によって処理
される。そのため、別途に乾燥時に発生するガス等の処
理設備を必要とせず、極めて有利である。更に、本件発
明では後燃焼ストーカ4上へ焼却灰Aを散布する構成と
しているため、乾燥ストーカ2や燃焼ストーカ3上に於
ける焼却物の燃焼状態に与える悪影響が殆ど無く、焼却
炉1の運転状態を常に良好な状態に保持できる。加え
て、各ストーカ2,3,4の下方より供給する燃焼用空
気の温度並びに風量を調整することにより、良好な燃焼
状態を保持しつつ焼却灰Aを効率よく乾燥させることが
でき、湿灰専用の乾燥機を設置する場合に比較して、助
燃燃料の消費も大幅に減少する。本発明は上述の通り、
優れた実用的効用を奏するものである。In the present invention, since the wet incineration ash A is dried by using the post-combustion stoker 4 of the stoker type incinerator, a wet ash drying device such as a rotary kiln and its associated equipment are completely eliminated. This eliminates the need for the equipment, simplifies the equipment, and eliminates the occurrence of problems such as wet ash sticking, which greatly improves the efficiency of drying and drying / melting incinerated ash. Further, water vapor, odor, etc. generated during the drying of the incineration ash A are mixed with the high temperature combustion gas in the incinerator 1 to be deodorized, and are also treated by the exhaust gas treatment device of the refuse incinerator. Therefore, it is extremely advantageous since it does not require a separate treatment facility for gas generated during drying. Further, in the present invention, since the incineration ash A is sprayed onto the post-combustion stoker 4, there is almost no adverse effect on the burning state of the incineration material on the dry stoker 2 and the combustion stoker 3, and the operation of the incinerator 1 The state can always be kept in good condition. In addition, by adjusting the temperature and the air volume of the combustion air supplied from below the respective stokers 2, 3 and 4, the incineration ash A can be efficiently dried while maintaining a good combustion state. Compared to the case where a dedicated dryer is installed, the consumption of auxiliary fuel is also greatly reduced. The present invention is as described above.
It has excellent practical utility.
【図1】本発明の実施に使用する湿った焼却灰の乾燥・
溶融プラントの構成説明図である。FIG. 1 Drying of wet incineration ash used in the practice of the present invention
It is a structure explanatory view of a melting plant.
【図2】焼却炉の縦断面概要図である。FIG. 2 is a schematic vertical sectional view of an incinerator.
【図3】図2のイーイ視断面図である。FIG. 3 is a sectional view taken along line E-I of FIG.
【図4】焼却炉のストーカ下部への燃焼用空気の供給系
統図である。FIG. 4 is a system diagram for supplying combustion air to the lower part of the stoker of the incinerator.
【図5】従前の乾燥灰取出し方式の焼却炉に付設した焼
却灰溶融プラントの説明図である。FIG. 5 is an explanatory diagram of an incinerator ash melting plant attached to a conventional incinerator of a dry ash extraction method.
【図6】従前の湿灰取出し方式の焼却炉に付設した焼却
灰乾燥・溶融プラントの説明図である。FIG. 6 is an explanatory view of an incinerator ash drying / melting plant attached to a conventional wet ash extraction type incinerator.
Aは焼却灰(湿灰)、Bは高温燃焼残渣、Cは乾燥灰、
Dは鉄分、Eは排ガス、Sは燃焼用空気、1は焼却炉、
1aは焼却灰供給口、2は乾燥ストーカ、3は燃焼スト
ーカ、4は後燃焼ストーカ、5は灰出しシュート、6は
ガスシールダンパー、7は助燃バーナ、8は乾灰振動ス
クリーン、9は乾灰移送コンベア、10は乾灰振動コン
ベア、11は磁選機、12,15,17はコンベア、1
3は灰溶融炉、14は金属バンカー、16は破砕機、1
8は焼却灰ピット、19は灰供給クレーン、20は灰ホ
ッパー、21は焼却灰供給プッシャー、22は焼却灰振
動スクリーン、23はコンベア、24はガスシールダン
パー、25は焼却灰導入シュート、26は灰分散装置、
26aは円筒体、26bはリブ、27は押込通風機、2
8は空気予熱器、29,30は風量調整用ダンパー。A is incineration ash (wet ash), B is high temperature combustion residue, C is dry ash,
D is iron, E is exhaust gas, S is combustion air, 1 is an incinerator,
1a is an incineration ash supply port, 2 is a dry stoker, 3 is a combustion stoker, 4 is a post-combustion stoker, 5 is an ash discharge chute, 6 is a gas seal damper, 7 is an auxiliary combustion burner, 8 is a dry ash vibrating screen, and 9 is dry. Ash transfer conveyor, 10 is a dry ash vibration conveyor, 11 is a magnetic separator, 12, 15, 17 are conveyors, 1
3 is an ash melting furnace, 14 is a metal bunker, 16 is a crusher, 1
8 is an incineration ash pit, 19 is an ash supply crane, 20 is an ash hopper, 21 is an incineration ash supply pusher, 22 is an incineration ash vibrating screen, 23 is a conveyor, 24 is a gas seal damper, 25 is an incineration ash introduction chute, and 26 is Ash disperser,
26a is a cylindrical body, 26b is a rib, 27 is a forced draft fan, 2
8 is an air preheater, 29 and 30 are air volume adjustment dampers.
Claims (5)
をストーカ式焼却炉(1)の後燃焼ストーカ(4)上へ
散布し、後燃焼ストーカ(4)上の燃焼残渣(B)と混
合せしめて焼却灰(A)を乾燥せしめると共に、前記燃
焼残渣(B)と乾燥せしめた焼却灰(A)とを乾燥状態
で焼却炉(1)外へ取り出すことを特徴とする焼却灰の
乾燥方法。1. Incinerator ash (A) discharged from other incinerators, etc.
Is sprayed onto the post-combustion stoker (4) of the stoker incinerator (1) and mixed with the combustion residue (B) on the post-combustion stoker (4) to dry the incineration ash (A), and at the same time, the combustion residue (B) and dried incineration ash (A) are taken out to the outside of an incinerator (1) in a dry state, The incinerator ash drying method characterized by the above-mentioned.
口(1a)を形成し、当該焼却灰供給口(1a)に設け
た灰分散装置(26)により、焼却灰(A)を後燃焼ス
トーカ(4)の燃焼残渣(B)上へ散布するようにした
請求項1に記載の焼却灰の乾燥方法。2. The incinerator ash (A) is formed by forming an incinerator ash supply port (1a) above the furnace side wall of the incinerator (1) and using an ash dispersion device (26) provided at the incinerator ash supply port (1a). The method for drying incinerated ash according to claim 1, wherein the composition is sprayed onto the combustion residue (B) of the post-combustion stoker (4).
(1a)を形成し、当該焼却灰供給口(1a)より直接
若しくは灰分散装置(26)を介して焼却灰(A)を後
燃焼ストーカ(4)の燃焼残渣(B)上へ散布するよう
にした請求項1に記載の焼却灰の乾燥方法。3. An incinerator ash supply port (1a) is formed on a furnace ceiling wall of the incinerator (1), and the incinerated ash (A) is directly supplied from the incinerator ash supply port (1a) or through an ash dispersion device (26). The method for drying incinerated ash according to claim 1, wherein the) is sprayed onto the combustion residue (B) of the post-combustion stoker (4).
る燃焼用空気の温度を任意に調整し、後燃焼ストーカ
(4)上へ散布した焼却灰(A)を高温熱風により通気
乾燥するようにした請求項1に記載の焼却灰の乾燥方
法。4. The incineration ash (A) sprinkled on the post-combustion stoker (4) is aerated and dried by hot air by adjusting the temperature of the combustion air supplied from below the post-combustion stoker (4) arbitrarily. The method for drying incinerated ash according to claim 1, wherein the ash is dried.
(A)をストーカ式焼却炉(1)の後燃焼ストーカ
(4)上へ散布して焼却灰(A)を乾燥せしめると共
に、後燃焼ストーカ(4)上の燃焼残渣(B)と乾燥せ
しめた焼却灰(A)とを乾燥状態で焼却炉(1)外へ取
り出し、更に鉄分(D)を除去したあとの乾燥灰(C)
を灰溶融炉(13)内へ供給するようにした焼却灰の溶
融処理方法。5. The incinerator ash (A) discharged from another incinerator or the like is sprayed onto the post-combustion stoker (4) of the stoker type incinerator (1) to dry the incinerator ash (A), and at the same time. The combustion residue (B) on the combustion stoker (4) and the dried incineration ash (A) are taken out of the incinerator (1) in a dry state, and the iron ash (D) is further removed to obtain the dried ash (C).
Is a method for melting incineration ash so that the ash is supplied into the ash melting furnace (13).
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP32704891A JP2747951B2 (en) | 1991-11-14 | 1991-11-14 | Drying method and melting method of incinerated ash |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP32704891A JP2747951B2 (en) | 1991-11-14 | 1991-11-14 | Drying method and melting method of incinerated ash |
Publications (2)
Publication Number | Publication Date |
---|---|
JPH05133515A true JPH05133515A (en) | 1993-05-28 |
JP2747951B2 JP2747951B2 (en) | 1998-05-06 |
Family
ID=18194728
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
JP32704891A Expired - Fee Related JP2747951B2 (en) | 1991-11-14 | 1991-11-14 | Drying method and melting method of incinerated ash |
Country Status (1)
Country | Link |
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JP (1) | JP2747951B2 (en) |
Cited By (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
EP0627270A1 (en) * | 1993-06-01 | 1994-12-07 | Hitachi Zosen Corporation | Ash melting furnace arrangement and method for supplying ash to ash melting furnace |
EP0683140A2 (en) * | 1994-05-17 | 1995-11-22 | Daido Tokushuko Kabushiki Kaisha | Method of processing a mixture of bottom ash and fly ash |
-
1991
- 1991-11-14 JP JP32704891A patent/JP2747951B2/en not_active Expired - Fee Related
Cited By (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
EP0627270A1 (en) * | 1993-06-01 | 1994-12-07 | Hitachi Zosen Corporation | Ash melting furnace arrangement and method for supplying ash to ash melting furnace |
EP0683140A2 (en) * | 1994-05-17 | 1995-11-22 | Daido Tokushuko Kabushiki Kaisha | Method of processing a mixture of bottom ash and fly ash |
EP0683140A3 (en) * | 1994-05-17 | 1996-04-10 | Daido Steel Co Ltd | Method of processing a mixture of bottom ash and fly ash. |
Also Published As
Publication number | Publication date |
---|---|
JP2747951B2 (en) | 1998-05-06 |
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