JPH0926124A - Melting treatment method of refuse incineration ash and melting treatment installation - Google Patents

Melting treatment method of refuse incineration ash and melting treatment installation

Info

Publication number
JPH0926124A
JPH0926124A JP17836795A JP17836795A JPH0926124A JP H0926124 A JPH0926124 A JP H0926124A JP 17836795 A JP17836795 A JP 17836795A JP 17836795 A JP17836795 A JP 17836795A JP H0926124 A JPH0926124 A JP H0926124A
Authority
JP
Japan
Prior art keywords
melting
incinerator
high temperature
waste
ash
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Granted
Application number
JP17836795A
Other languages
Japanese (ja)
Other versions
JP2950754B2 (en
Inventor
Seizo Katsui
征三 勝井
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.)
Plantec Inc
Original Assignee
Plantec Inc
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 Plantec Inc filed Critical Plantec Inc
Priority to JP17836795A priority Critical patent/JP2950754B2/en
Publication of JPH0926124A publication Critical patent/JPH0926124A/en
Application granted granted Critical
Publication of JP2950754B2 publication Critical patent/JP2950754B2/en
Anticipated expiration legal-status Critical
Expired - Fee Related legal-status Critical Current

Links

Abstract

PROBLEM TO BE SOLVED: To provide an installation which is high in thermal efficiency, small in power consumption, simple in structure and seldom to cause breakdown, and to make the best use of high carolific value waste matter, and generate molten slag having stabilized properties. SOLUTION: An ordinary refuse incinerator 1 which specifically burns ordinal refuse from which high temperature carolific value waste matter is separately removed is combined with a high temperature incinerator 4 which exclusively burns high carolific value waste. A high temperature furnace exhaust gas 62 in an imperfect combustion state discharged from the high temperature incinerator 4 is secondarily burnt in a secondary combustion chamber 46 located above a melting device 3 to produce a melting device gas 63. By using the radiation heat of this melting device gas 63, incinerated ashes 81 discharged from the ordinal refuse incinerator 1 and the high temperature incinerator 4 are processed by melting.

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、一般廃棄物や産業
廃棄物を焼却するごみ焼却施設において、該ごみ焼却施
設から排出されるごみ焼却灰の溶融処理方法及び溶融処
理設備に関する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a melting treatment method and a melting treatment facility for refuse incineration ash discharged from a refuse incineration facility for incinerating general waste or industrial waste.

【0002】[0002]

【従来の技術】平成4年10月施行の改正廃棄物処理法
により、ごみ焼却施設の集じん設備で捕集される飛灰
は、重金属類を含んでいるために、溶融、セメント固
化、薬剤処理、酸抽出の4方法の何れかで安定化処理す
ることが規定された。
2. Description of the Related Art According to the revised Waste Management Law of October 1992, the fly ash collected in the dust collection facility of a refuse incineration facility contains heavy metals, which causes melting, cement solidification, and chemical treatment. It was specified that the stabilization treatment should be performed by any one of the four methods of treatment and acid extraction.

【0003】そのため、排出される焼却灰の容積低減化
と併せて、含有する重金属類の封入化を目的として、上
記飛灰と共に焼却灰を溶融固化する方法が脚光を浴びて
きた。
Therefore, a method of melting and solidifying the incinerated ash together with the fly ash has been in the limelight for the purpose of encapsulating the heavy metals contained therein as well as reducing the volume of the incinerated ash discharged.

【0004】現在、実用に供されている灰溶融炉の形式
としては、焼却炉との関係位置による分類では、焼却灰
排出口に直接結合される直結形と、焼却炉から排出され
た湿灰を一旦灰ホッパ等に貯留したのち処理する別置形
とがあり、熱源による分類では、バーナを使用する表面
溶融炉(内部溶融型)と、プラズマ炉、アーク炉や電気
抵抗炉等の電気を熱源とする方式に大別できる。
At present, as the types of ash melting furnaces which are practically used, according to the position related to the incinerator, there are a direct connection type directly connected to the incinerator ash discharge port and a wet ash discharged from the incinerator. There is a separate type that temporarily stores the ash in an ash hopper, etc., and then treats it according to the heat source, such as surface melting furnace using burner (internal melting type) and plasma furnace, arc furnace, electric resistance furnace, etc. Can be roughly divided into the following methods.

【0005】以下、図6にその概略構造を示す直結形表
面溶融炉と、図7にその概略構造を示す別置形プラズマ
溶融炉とを、従来の代表例として説明する。
A direct-connection type surface melting furnace whose schematic structure is shown in FIG. 6 and a separate type plasma melting furnace whose schematic structure is shown in FIG. 7 will be described below as typical examples.

【0006】図6の直結形表面溶融炉において、ホッパ
aから投入された通常のごみb1は、回転キルンc内に
おいて、図示しない燃焼用空気予熱器により昇温された
燃焼用空気d1によって乾燥・燃焼され、発生する排ガ
スe1は再燃焼室fに上昇し、金属等の不燃物を含む焼
却残渣b2は、後燃焼火格子g上を送られながら、同じ
く燃焼用空気d1により、残存する未燃物が更に乾燥・
燃焼されて焼却灰hとなり、溶融装置Mに落下する。
In the direct-coupling type surface melting furnace shown in FIG. 6, the normal dust b1 introduced from the hopper a is dried in the rotary kiln c by the combustion air d1 heated by the combustion air preheater (not shown). The exhaust gas e1 that is burned and generated rises to the re-combustion chamber f, and the incineration residue b2 containing incombustibles such as metals is sent over the post-combustion grate g, while remaining unburned due to the combustion air d1. Things are even more dry
It is burned to form incineration ash h and falls into the melting device M.

【0007】後燃焼火格子g上で後燃焼されたとはい
え、上述の燃焼灰h中には、なお、12〜15%程度の
遊離炭素を含む可燃物が残存する(熱灼減量換算30〜
60%)ように制御されており、この可燃分が溶融時の
内部熱源となる。
Although post-combusted on the post-combustion grate g, combustible substances containing about 12 to 15% of free carbon still remain in the above-mentioned combustion ash h.
60%), and this combustible component becomes an internal heat source during melting.

【0008】セラミックス等の耐火材で構成された炉床
M1に堆積された焼却灰hは、プッシャM2で少量ずつ
押出されながら前進し、天井部に配設されたバーナM3
による加熱と、後述する炉床下部から圧送される高温の
溶融用燃焼空気d2とにより、前述の残存可燃分が着火
燃焼を始め、1200〜1500℃に昇温して表面から
溶融する。
The incineration ash h deposited on the hearth M1 made of a refractory material such as ceramics is pushed forward little by little by the pusher M2, and is advanced to the burner M3 installed on the ceiling.
And the high-temperature melting combustion air d2 that is pressure-fed from the lower part of the hearth described below, the above-mentioned residual combustible component starts igniting and burning, and is heated to 1200 to 1500 ° C. and melted from the surface.

【0009】溶融した溶融スラグS1は、落下管M4か
ら水封コンベアj中に滴下し、急冷破砕されて水砕スラ
グS2となり、図示しない場外に搬出されるようになさ
れている。
The melted molten slag S1 is dropped from the drop pipe M4 into the water-sealed conveyor j, rapidly crushed and crushed to form a water-crushed slag S2, which is carried out to the outside (not shown).

【0010】ここで、溶融装置M内で発生した高温の排
ガスe2は、排ガスファンk1により落下管M4部から
吸引されて、溶融炉送風機k2を備えた高温空気加熱器
k3において熱交換され、常温空気d3と混合して更に
減温されたのち、排ガスファンk1を経て再燃室fへと
排出される。
Here, the high temperature exhaust gas e2 generated in the melting apparatus M is sucked from the drop pipe M4 by the exhaust gas fan k1 and heat-exchanged in the high temperature air heater k3 equipped with the melting furnace blower k2 to obtain the room temperature. After being mixed with the air d3 and further cooled, it is discharged into the reburn chamber f through the exhaust gas fan k1.

【0011】また、前述の溶融用燃焼空気d2は、燃焼
用空気d1を溶融炉送風機k2で吸引し、高温空気加熱
器k3により、500℃前後まで昇温されたものであ
る。
Further, the above-mentioned melting combustion air d2 is obtained by sucking the combustion air d1 by the melting furnace blower k2 and raising the temperature to about 500 ° C. by the high temperature air heater k3.

【0012】次に、図7に示す別置形プラズマ溶融炉に
おいて、溶融装置Mは、水冷ジャケットM5に囲繞さ
れ、後述のプラズマ装置Pを装備した耐火物製の溶融槽
M6と、出滓口M7及び灰供給口M8、並びに図6と同
様の落下管M4とで構成されている。
Next, in the separate type plasma melting furnace shown in FIG. 7, the melting device M is surrounded by a water cooling jacket M5, and a refractory melting tank M6 equipped with a plasma device P to be described later and a slag outlet M7. And an ash supply port M8 and a drop pipe M4 similar to FIG.

【0013】また、プラズマ装置Pは、トランスファー
方式の例を示し、主体となるプラズマトーチP1(+
極)、下部電極P2(−極)と冷却水配管P3(+荷
電)、P4(−荷電)及びプラズマガス供給口P5並び
に図示しない点火装置やトーチ移動装置等からなり、各
電極は電源装置qに接続されている。
Further, the plasma device P shows an example of a transfer system, and the main plasma torch P1 (+
Electrode), lower electrode P2 (-electrode), cooling water pipes P3 (+ charged), P4 (-charged) and plasma gas supply port P5, and an ignition device, torch moving device, etc. not shown, and each electrode is a power supply device q. It is connected to the.

【0014】まず、磁選及び粉砕等の前処理をして、灰
ホッパn1に貯留された水分を保有する焼却灰hは、灰
供給フィーダn2により、灰供給口M8を経て溶解槽M
6に供給される。ここで、焼却灰h中には、図示しない
主煙道用集じん装置により捕集された飛灰を混入せしめ
ることもある。
First, the incineration ash h which retains the water stored in the ash hopper n1 after pretreatment such as magnetic separation and pulverization is passed through the ash supply port n8 by the ash supply feeder n2 and then melted into the melting tank M.
6. Here, fly ash collected by a dust collector for a main flue not shown may be mixed in the incinerated ash h.

【0015】次に、プラズマトーチP1の外周を冷却水
で冷却しつつ、プラズマガス供給口P5から不活性ガス
を供給し、プラズマトーチP1と下部電極P2との間に
直流電圧を印荷すれば、1万℃以上にも達するプラズマ
が発生し、溶融槽M6内の焼却灰hを溶融する。
Next, while cooling the outer periphery of the plasma torch P1 with cooling water, an inert gas is supplied from the plasma gas supply port P5, and a DC voltage is applied between the plasma torch P1 and the lower electrode P2. Plasma that reaches 10,000 ° C. or higher is generated to melt the incineration ash h in the melting tank M6.

【0016】溶融した溶融スラグS1は、溶融槽M6の
一部を切欠き、落下管M4側に傾斜した出滓口M7から
滴下し、落下管途中から噴出する常温の冷却空気d3に
より急冷されることにより破砕され、落下管M4の下方
に位置するスラグコンベアr内で冷却されて空冷スラグ
S3となり、図示しない場外に搬出されるようになされ
ている。ここで溶融スラグS1の冷却方式を図6に示す
ような水噴射方式とし、水砕スラグS2として搬出する
方式もある。
The molten molten slag S1 is formed by notching a part of the melting tank M6, dropping it from a slag outlet M7 inclined to the side of the drop pipe M4, and rapidly cooling it by cooling air d3 at room temperature which is jetted from the middle of the drop pipe. As a result, it is crushed and cooled in the slag conveyor r located below the drop pipe M4 to become air-cooled slag S3, which is carried out to the outside (not shown). Here, there is also a system in which the cooling system of the molten slag S1 is a water injection system as shown in FIG.

【0017】また、溶融装置M内で発生した高温の排ガ
スe2は、図示しない排ガスファンにより落下管M4部
から吸引されて、図示しないガス冷却装置及び溶融炉ガ
ス集じん装置を経て大気中に放出される。
Further, the high temperature exhaust gas e2 generated in the melting apparatus M is sucked from the drop pipe M4 by an exhaust gas fan (not shown) and discharged into the atmosphere through a gas cooling device (not shown) and a melting furnace gas dust collector. To be done.

【0018】[0018]

【発明が解決しようとする課題】上述のように直結形表
面溶融炉は、焼却灰中に残存する可燃分の燃焼熱とバー
ナの加熱により、焼却炉から排出された高温の焼却灰を
そのまま溶融する方式である。
As described above, the direct connection type surface melting furnace melts the high temperature incinerator ash discharged from the incinerator as it is due to the combustion heat of the combustible components remaining in the incinerator ash and the heating of the burner. It is a method to do.

【0019】従って、熱効率が高く、不燃物も一括して
溶融が可能であるという利点はあるが、残存可燃物量が
一定せず安定した高温が得にくいために、溶融スラグの
特性が不安定になるだけでなく、燃料費が増大するほ
か、高温の溶融用燃焼空気を必要とするために、高温空
気加熱器の高温腐食が避けられない。さらに、溶融装置
故障時には、ごみ焼却施設全体が停止するだけでなく、
復旧するまでは焼却灰の完全燃焼が期待できず、公害発
生のおそれがあるために、予備溶融装置等の非常時対策
が必要となるという問題があった。
Therefore, although there is an advantage that the thermal efficiency is high and the incombustibles can be melted collectively, the characteristics of the molten slag become unstable because the amount of the remaining combustibles is not constant and a stable high temperature is difficult to obtain. In addition to increasing fuel cost, high temperature combustion air for melting is required, and high temperature corrosion of the high temperature air heater is unavoidable. Furthermore, not only is the entire refuse incineration facility stopped when a melting device fails,
Until the restoration, the incineration ash cannot be expected to be completely burned, and there is a risk of pollution, so there was a problem that emergency measures such as a preliminary melting device were necessary.

【0020】これに対して、別置形プラズマ溶融炉は、
焼却施設から排出された湿灰中の鉄分を除去し、粉砕し
た細粒灰を灰ホッパ等に一旦貯留したのち、別置の溶融
炉のプラズマ熱により溶融する方式である。
On the other hand, the separate plasma melting furnace is
This is a method in which the iron content in the wet ash discharged from the incinerator is removed, the crushed fine ash is once stored in an ash hopper, etc., and then melted by the plasma heat of a separate melting furnace.

【0021】従って、プラズマ出力調整等の操作性が良
く、安定した高温が得られるために、溶融スラグの特性
が向上する反面、湿灰乾燥と溶融のために多大の電力を
消費するうえに、建設費が高価であるために、ごみ発電
設備を有しない施設には不向きであり、さらに前処理装
置のみでなく、除去した鉄分や排ガスの処理装置が別途
に必要であるという問題があった。
Therefore, the operability of adjusting the plasma output and the like is good and a stable high temperature is obtained, so that the characteristics of the molten slag are improved, but on the other hand, in addition to consuming a large amount of power for the wet ash drying and melting, Since the construction cost is high, it is not suitable for a facility that does not have a waste power generation facility, and there is a problem that not only a pretreatment device but also a treatment device for removed iron and exhaust gas is separately required.

【0022】[0022]

【課題を解決するための手段】本発明の請求項1記載の
ごみ焼却灰の溶融処理方法は、高発熱量の廃棄物を分別
除去した通常ごみ焼却炉と、高発熱量の廃棄物を専焼す
る高温焼却炉とを併設し、高温焼却炉で発生する高温の
ガス体の放射熱を利用し、通常ごみ焼却炉及び高温焼却
炉から排出される焼却灰を溶融処理するものである。
According to a first aspect of the present invention, there is provided a method for melting refuse incineration ash by melting, wherein an ordinary refuse incinerator in which waste having a high calorific value is separated and removed and a waste having a high calorific value is exclusively burned. A high-temperature incinerator is also installed, and the radiant heat of the high-temperature gas generated in the high-temperature incinerator is used to melt and process the incineration ash normally discharged from the refuse incinerator and the high-temperature incinerator.

【0023】本発明の請求項2記載のごみ焼却灰の溶融
処理方法は、前記ガス体を、2次燃焼用の酸素または2
次空気量の制御により所定範囲の温度に保持する。
In the method for melting refuse incinerated ash according to claim 2 of the present invention, the gas body is treated with oxygen or 2 for secondary combustion.
The temperature is maintained within a predetermined range by controlling the amount of secondary air.

【0024】本発明の請求項3記載のごみ焼却灰の溶融
処理設備は、高発熱量の廃棄物を分別除去した通常ごみ
焼却炉と、高発熱量の廃棄物を専焼する高温焼却炉とを
併設したごみ焼却灰の溶融処理設備であって、前記通常
ごみ焼却炉の下流に溶融装置が設けられ、該溶融装置の
上方に前記高温焼却炉の2次燃焼室が設けられたもので
ある。
The facility for melting waste incinerated ash according to claim 3 of the present invention comprises a normal waste incinerator in which waste having a high calorific value is separated and removed, and a high temperature incinerator for exclusively burning a waste in a high calorific value. The waste incineration ash melting treatment facility is provided side by side with a melting device provided downstream of the normal waste incinerator, and a secondary combustion chamber of the high temperature incinerator provided above the melting device.

【0025】本発明の請求項4記載のごみ焼却灰の溶融
処理設備は、請求項3記載のごみ焼却灰の溶融処理設備
において、前記高温焼却炉から排出される焼却灰を前記
通常ごみ焼却炉に搬入する搬出手段が設けられたもので
ある。
According to a fourth aspect of the present invention, in the refuse incineration ash melting treatment facility, in the waste incineration ash melting treatment facility in claim 3, the incinerator ash discharged from the high temperature incinerator is in the normal waste incinerator. The carrying-out means for carrying in is provided.

【0026】[0026]

【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.

【0027】図1は、本発明に係るごみ焼却灰の溶融処
理設備の概要を示す断面図であり、図2は溶融装置周辺
の概要を示す拡大断面図である。
FIG. 1 is a sectional view showing an outline of a refuse incineration ash melting treatment facility according to the present invention, and FIG. 2 is an enlarged sectional view showing an outline of the vicinity of a melting apparatus.

【0028】図1及び図2において、符号1は通常ごみ
焼却炉であり、通常の築炉構造である焼却炉本体11
と、ごみ投入ホッパ12、乾燥火格子13、燃焼火格子
14、後燃焼火格子15、各火格子下ホッパ群16及び
反射壁17並びに2次空気吹込孔18と、冷却空気ノズ
ル19とにより構成されている。
In FIGS. 1 and 2, reference numeral 1 is a normal refuse incinerator, and an incinerator main body 11 having a normal furnace construction structure.
And a dust introduction hopper 12, a dry grate 13, a combustion grate 14, a post-combustion grate 15, a lower hopper group 16 of each grate, a reflecting wall 17, a secondary air blowing hole 18, and a cooling air nozzle 19. Has been done.

【0029】通常ごみ焼却炉1のガス排出口には、整流
壁21、再燃焼室22及びガス冷却室23より成るガス
冷却設備2が連接され、上述の反射壁背部に形成される
再燃焼室底部には、後燃焼火格子15上に位置する如く
飛灰落下孔24が貫通されている。
Normally, the gas outlet of the refuse incinerator 1 is connected to the gas cooling equipment 2 including the flow straightening wall 21, the reburning chamber 22 and the gas cooling chamber 23, and the reburning chamber formed on the back of the above-mentioned reflecting wall. A fly ash drop hole 24 penetrates through the bottom so as to be located on the post-combustion grate 15.

【0030】後燃焼火格子15の前方には溶融装置3が
連接されている。溶融装置3は、図2に示すように、L
字形断面の耐火物製で、水平部の中央部表面が前方に傾
斜した溶融段31と、溶融段水平部を摺動するプッシャ
32及び、上端に冷却ノズル33を備えた水冷ジャケッ
トから成る落下管34で構成され、溶融段31の前端は
溶融灰滴下部35となる。
The melting device 3 is connected in front of the post-combustion grate 15. As shown in FIG.
A drop tube made of a refractory having a V-shaped cross section, and including a melting stage 31 in which the central surface of the horizontal part is inclined forward, a pusher 32 sliding on the horizontal part of the melting stage, and a water cooling jacket having a cooling nozzle 33 at the upper end. 34, and the front end of the melting stage 31 becomes a molten ash dropping section 35.

【0031】符号4は、廃プラスチック等の高発熱量ご
みの専焼炉としての高温焼却炉であり、炉本体41、プ
ラスチックホッパ42、火格子43及び、輻射壁44と
2次燃焼ノズル45とを有し、上述の溶融装置3の上方
に位置する2次燃焼室46とから構成されている。
Reference numeral 4 is a high-temperature incinerator as a dedicated incinerator for wastes with high calorific value, such as waste plastic, which comprises a furnace body 41, a plastic hopper 42, a grate 43, a radiation wall 44 and a secondary combustion nozzle 45. And the secondary combustion chamber 46 located above the melting device 3 described above.

【0032】つまり、通常ごみ焼却炉1と高温焼却炉4
とは溶融装置3及び2次燃焼室46で連通された状態で
併設されている。
That is, the normal refuse incinerator 1 and the high temperature incinerator 4
Are installed side by side in a state of being connected to each other by the melting device 3 and the secondary combustion chamber 46.

【0033】前記落下管34の下方には、スラグコンベ
ア51を内蔵する湿式の灰搬出装置52が配設され、落
下管34の下端を水封するようになされている。
Below the drop pipe 34, a wet ash carrying-out device 52 having a slag conveyor 51 built therein is disposed, and the lower end of the drop pipe 34 is water-sealed.

【0034】また、火格子下ホッパ群16の下方には、
各ホッパからの落じんを排出する落じんコンベア53が
配設され、高温焼却炉4の火格子43の下方には、排出
される焼却灰を輸送する焼却灰コンベア54が接続され
ており、落じんコンベア53と焼却灰コンベア54の終
端は、夫々灰コンベア55に接続されている。
Below the grate lower hopper group 16,
A drop dust conveyor 53 for discharging the dust from each hopper is arranged, and an incinerator ash conveyor 54 for transporting the incinerated ash to be discharged is connected below the grate 43 of the high temperature incinerator 4, and The ends of the dust conveyor 53 and the incineration ash conveyor 54 are connected to the ash conveyor 55, respectively.

【0035】灰コンベア55は、焼却炉本体11の側壁
に沿って上方に搬送物を搬送し、終端が後燃焼火格子1
5の上方に開口する灰落下口56(図2参照)に接続さ
れている。
The ash conveyor 55 conveys the conveyed objects upward along the side wall of the incinerator body 11, and the end thereof is the post-combustion grate 1.
5 is connected to an ash drop port 56 (see FIG. 2) that opens upward.

【0036】上述した焼却灰コンベア54と灰コンベア
55とによって、高温焼却炉4から排出される焼却残渣
を通常ごみ焼却炉1に搬入する搬出手段を構成してい
る。
The incineration ash conveyor 54 and the ash conveyor 55 described above constitute an unloading means for loading the incineration residue discharged from the high temperature incinerator 4 into the normal refuse incinerator 1.

【0037】次に、上述のように構成されたごみ焼却灰
の溶融処理設備によって行う溶融処理方法について説明
する。
Next, a melting processing method carried out by the melting incineration ash melting processing facility configured as described above will be described.

【0038】図3及び図4は、本設備におけるごみ、排
ガス、空気及び灰とスラグの概略の流れを示す説明図で
ある。
3 and 4 are explanatory views showing the general flow of dust, exhaust gas, air, ash, and slag in this equipment.

【0039】プラスチック類等の高発熱量ごみ61は、
プラスチックホッパ42から炉本体41に投入され、図
示しないバーナで着火されるとともに、図示しない空気
予熱器で予熱された高温炉燃焼空気71を供給されて激
しく燃焼して、不完全燃焼状態の高温炉排ガス62(未
燃焼ガス)を発生し、2次燃焼室46に向う。該高温炉
排ガス62は、2次燃焼室46上部の2次燃焼ノズル4
5から供給される酸素または図示しない空気予熱器で昇
温された2次空気72により2次燃焼を起こして溶融装
置ガス63となり、発生する高熱を輻射壁44で溶融段
31に放射したのち、後燃焼火格子15上を焼却炉本体
11へと流入する。
The high calorific value waste 61 such as plastics is
The high-temperature furnace combustion air 71, which is put into the furnace main body 41 from the plastic hopper 42, is ignited by a burner (not shown), and is preheated by an air preheater (not shown), burns violently to incompletely burn the high-temperature furnace. Exhaust gas 62 (unburned gas) is generated and goes to the secondary combustion chamber 46. The high temperature furnace exhaust gas 62 is discharged from the secondary combustion nozzle 4 above the secondary combustion chamber 46.
After the secondary combustion is caused by the oxygen supplied from 5 or the secondary air 72 whose temperature is raised by the air preheater (not shown) to become the melting device gas 63, and the generated high heat is radiated to the melting stage 31 by the radiation wall 44, It flows into the incinerator body 11 on the post-combustion grate 15.

【0040】この際、図示しない制御装置で酸素または
2次空気72の供給量を制御することにより、溶融装置
ガス63は焼却灰溶融に必要な約1400℃以上に保持
される。このように、溶融装置ガス63の温度を制御す
ることで、溶融装置3の温度が所定範囲に保持され、こ
のために直結形表面溶融炉の如く焼却灰中の残存可燃物
量に左右されることなく、安定した高温が得られ、後述
する溶融スラグの特性を安定させることができる。
At this time, the melter gas 63 is maintained at about 1400 ° C. or higher required for melting the incineration ash by controlling the supply amount of oxygen or the secondary air 72 by a controller (not shown). In this way, by controlling the temperature of the melting device gas 63, the temperature of the melting device 3 is maintained within a predetermined range, and as a result, it depends on the amount of residual combustibles in the incineration ash as in a direct-coupling type surface melting furnace. Therefore, a stable high temperature can be obtained, and the characteristics of the molten slag described later can be stabilized.

【0041】一方、収集段階において、上述の高発熱量
廃棄物のほか、瓶、缶類も分別除去された通常ごみ64
は、ホッパ12から通常ごみ焼却炉1内に投入され、乾
燥火格子13及び燃焼火格子14上を順次下方に送られ
る。そこで、図示しない空気予熱器で予熱された通常炉
燃焼空気73を供給され、前述の溶融装置ガス63と焼
却炉本体11が保有する燃焼熱とを受けることにより、
乾燥・燃焼されて排ガス65を発生させ、残余は焼却灰
81となって、後燃焼火格子15上に落下する。
On the other hand, in the collection stage, in addition to the above-mentioned high calorific value waste, bottles and cans are separated by normal waste 64
Is usually put into the refuse incinerator 1 from the hopper 12, and is sent downward on the dry grate 13 and the combustion grate 14 in order. Then, by supplying the normal furnace combustion air 73 preheated by an air preheater (not shown) and receiving the above-described melting device gas 63 and the combustion heat held by the incinerator body 11,
It is dried and burned to generate the exhaust gas 65, and the rest becomes incineration ash 81, which falls on the post-combustion grate 15.

【0042】次に、後燃焼火格子15の前段では、焼却
灰81は、その中に残存する難燃物を上記と同様の状態
でおき燃焼されたのち、後燃焼火格子15の後段に移送
され、該後段下部には火格子下ホッパからの空気の流通
がないために冷却されることなく、前述の溶融装置ガス
63の照射を受けて昇温し、溶融段31に落下する。
Next, in the front stage of the post-combustion grate 15, the incineration ash 81 is burned with the flame-retardant material remaining therein in the same state as above, and then transferred to the rear stage of the post-combustion grate 15. Then, since there is no air flow from the hopper below the grate in the lower part of the latter stage, it is not cooled and is irradiated with the above-mentioned melting device gas 63 to rise in temperature and falls into the melting stage 31.

【0043】溶融段31に落下した高温の焼却灰81
は、上述の溶融装置ガス63の高熱により溶融状態とな
り、プッシャ32により、少量ずつ前方に押出されなが
ら、溶融段31の傾斜に沿って流下し、溶融灰82とな
って溶融灰滴下部35から落下管34内に滴下する。
High-temperature incinerated ash 81 dropped on the melting stage 31
Becomes a molten state due to the high heat of the above-described melting device gas 63, and while being pushed forward little by little by the pusher 32, it flows down along the inclination of the melting stage 31 and becomes molten ash 82 from the molten ash dropping section 35. Drop into the drop tube 34.

【0044】この滴下する溶融灰82を、冷却ノズル3
3から噴出するスラグ冷却用の水または空気74で急冷
・破砕して冷却スラグ83とし、冷却スラグ83は灰搬
出装置52内に落下してさらに冷却された後、スラグコ
ンベア51により装置外に搬出される。
The molten ash 82 to be dropped is supplied to the cooling nozzle 3
3 is rapidly cooled and crushed with water or air 74 for cooling the slag to form a cooling slag 83. The cooling slag 83 drops into the ash discharging device 52 and is further cooled, and then is discharged outside the device by the slag conveyor 51. To be done.

【0045】また、各火格子から火格子下ホッパ16に
落下した落じん84は、落じんコンベア53により移送
される。また、炉本体41内で燃焼された高発熱量ごみ
61の残渣である高温焼却灰85は、火格子43を開閉
することにより高温焼却炉4から排出され、焼却灰コン
ベア54で移送されたのち、前述の落じん84と共に、
灰コンベア55によって持上げられ、後燃焼火格子15
の上方に位置する灰落下口56から、焼却炉本体11内
に投下され、落じん84及び高温焼却灰85中の未燃物
が、前述の焼却灰81上で完全に焼却される。このよう
に、高温焼却灰85を焼却炉本体11内に投下するの
は、溶融装置ガス63が十分な高熱を保つためには、高
温炉排ガス62は未燃焼状態でなければならないため、
高発熱量ごみ61は不完全燃焼となり、この結果、高温
焼却灰85中の未燃物が増加するからである。つまり、
高温焼却灰85中の未燃物を減少させるように高温焼却
炉4を燃焼制御すれば、焼却灰の溶融を行うに十分な溶
融装置ガス63を生成することができない。このため、
高温焼却灰85を焼却炉本体11内に投下して高温焼却
灰85の未燃物を燃焼させる必要がある。
Dust 84 dropped from each grate to the grate lower hopper 16 is transferred by a dust conveyor 53. Further, the high temperature incineration ash 85, which is the residue of the high calorific value dust 61 burned in the furnace body 41, is discharged from the high temperature incinerator 4 by opening and closing the grate 43, and is transferred by the incineration ash conveyor 54. , Along with the above-mentioned drop dust 84,
Lifted by the ash conveyor 55, the post combustion grate 15
From the ash drop port 56 located above, the unburned materials in the dust 84 and the high temperature incinerated ash 85 are completely incinerated on the incinerated ash 81 described above. Thus, the high temperature incineration ash 85 is dropped into the incinerator body 11 because the high temperature furnace exhaust gas 62 must be in an unburned state in order for the melting apparatus gas 63 to maintain a sufficiently high heat.
This is because the high calorific value waste 61 is incompletely burned, and as a result, the amount of unburned matter in the high temperature incineration ash 85 increases. That is,
If combustion control of the high temperature incinerator 4 is performed so as to reduce unburned substances in the high temperature incineration ash 85, it is not possible to generate the melting device gas 63 sufficient to melt the incineration ash. For this reason,
It is necessary to drop the high temperature incineration ash 85 into the incinerator body 11 to burn the unburned matter of the high temperature incineration ash 85.

【0046】一方、溶融段31の上方に位置する2次燃
焼室46に吹込まれ、焼却灰81の溶融を行った高温の
溶融装置ガス63は、冷却空気ノズル19から炉内に吹
込まれる冷却空気75及び反射壁17を冷却後、同じく
焼却炉本体11内に吹込まれる反射壁冷却空気76によ
り冷却されたのち、ごみ層から発生する排ガス65と混
合して混合ガス66となる。
On the other hand, the high-temperature melting apparatus gas 63 blown into the secondary combustion chamber 46 located above the melting stage 31 to melt the incineration ash 81 is blown into the furnace from the cooling air nozzle 19. After cooling the air 75 and the reflecting wall 17, the air 75 and the reflecting wall 17 are also cooled by the reflecting wall cooling air 76 blown into the incinerator body 11 and then mixed with the exhaust gas 65 generated from the dust layer to form the mixed gas 66.

【0047】混合ガス66は、その後、通常炉2次空気
77で2次燃焼されたのち、再燃焼室22に送られ、残
存する未燃ガスの再燃焼を完了して、ガス冷却室23に
送られる。
After that, the mixed gas 66 is secondarily burned by the secondary air 77 of the normal furnace, and then sent to the reburning chamber 22 to complete the reburning of the remaining unburned gas to the gas cooling chamber 23. Sent.

【0048】また、焼却炉本体11及び再燃焼室22内
に浮遊する飛灰のうち、比較的重いものは、再燃焼室2
2内でのガス反転の際にガス流から分離し、落下飛灰8
6として、飛灰落下孔24から後燃焼火格子15上に落
下して、前述の落じん84、高温焼却灰85と共におき
燃焼される。
Of the fly ash floating in the incinerator body 11 and the reburning chamber 22, the relatively heavy one is the reburning chamber 2
During the gas reversal in 2, it is separated from the gas flow and falls 8
6, it falls from the fly ash drop hole 24 onto the post-combustion grate 15 and is burnt together with the above-mentioned dust 84 and high-temperature incinerated ash 85.

【0049】図5は、上述と別の形態を示し、上述と同
様の部材には同一の符号を付して説明を省略する。
FIG. 5 shows a different form from the above, in which the same members as those described above are designated by the same reference numerals and the description thereof is omitted.

【0050】図5において、上述との主なる相違点は、
溶融段31の次に後述する溶解槽91を設置するととも
に、高温焼却炉4からでる高温炉排ガス62を煙道92
を介して送入する点である。
In FIG. 5, the main difference from the above is that
A melting tank 91, which will be described later, is installed next to the melting stage 31, and the high temperature furnace exhaust gas 62 discharged from the high temperature incinerator 4 is flue 92.
It is a point to send via.

【0051】溶解槽91は、耐火物製で上部が解放さ
れ、底部にはメタル滞積用傾斜部を有し、上端の一方に
は出滓口93が切欠かれている。
The melting tank 91 is made of refractory and has an open top, a bottom with an inclined portion for metal accumulation, and a slag opening 93 cut out at one of the upper ends.

【0052】溶解槽91内においては、鉄分等は底部の
メタル滞積用傾斜部に分離沈澱し、比較的軽量のSi,
Ca,Al等の酸化物は上層に浮上し、溶融灰82が一
定レベルに到達すれば、出滓口93から落下管34側に
滴下するようになされている。
In the melting tank 91, iron and the like are separated and settled at the bottom metal accumulation slope portion, so that relatively light weight Si,
Oxides such as Ca and Al float to the upper layer, and when the molten ash 82 reaches a certain level, it drops from the outlet 93 to the drop pipe 34 side.

【0053】この溶解槽91は、前述した図1乃至図4
に示す溶融処理設備に設けることもできる。
The melting tank 91 is the same as that shown in FIGS.
It can also be installed in the melt processing equipment shown in.

【0054】なお、本説明において、高温焼却炉4は、
固定炉型の物を図示したが、型式は何れでもよく、スラ
グ冷却は2次燃焼室の温度及び、スラグの再利用形態に
よって方式を決定すればよく、灰搬出装置52は湿式で
説明したが、乾式でもよい。
In this description, the high temperature incinerator 4 is
Although the fixed furnace type is illustrated, any type may be used, and the slag cooling may be determined by the temperature of the secondary combustion chamber and the reuse form of the slag, and the ash discharging device 52 has been described as a wet type. It may be dry.

【0055】また、通常ごみ焼却炉1から排出される図
示しない排ガス処理装置で捕集された飛灰を同時処理し
てもよく、落じん84、高温焼却灰85を上記捕集飛灰
と共に別途処理する方式でも差支えない。
Further, the fly ash collected from an exhaust gas treatment device (not shown) normally discharged from the refuse incinerator 1 may be simultaneously treated, and the dust 84 and the high temperature incinerated ash 85 are separately collected together with the above-mentioned collected fly ash. It does not matter which method is used.

【0056】[0056]

【発明の効果】以上述べたように、請求項1記載のごみ
焼却灰の溶融処理方法によれば、焼却炉から排出された
乾灰を高温のまま溶融する方式であるために、熱効率が
高く、別途処理すべき高発熱ごみの燃焼熱を溶融に利用
する有効利用法であり、電力使用量が少ない経済的な方
法を提供することができる。また、高温の溶融装置ガス
にさらされる部位は溶融装置内のみであり、高熱対策を
要する範囲が局限できるだけでなく、溶融装置ガスは、
通常ごみ焼却炉側で処理できるために、特別の排ガス処
理装置を必要としない。
As described above, according to the melting incineration ash melting method of the first aspect, the dry ash discharged from the incinerator is melted at a high temperature, so that the thermal efficiency is high. It is an effective utilization method of utilizing the combustion heat of high-heat-generation waste to be separately treated for melting, and can provide an economical method of using a small amount of electric power. Moreover, the part exposed to the high-temperature melting device gas is only in the melting device, and not only the range requiring high heat countermeasures can be localized, but the melting device gas is
No special exhaust gas treatment equipment is required because the waste can be treated on the incinerator side.

【0057】請求項2記載のごみ焼却灰の溶融処理設備
によれば、ガス体を、2次燃焼用の酸素または2次空気
量の制御により所定範囲の温度に保持することで、直結
形表面溶融炉の如く焼却灰中の残存可燃物量に左右され
ることなく、安定した高温が得られ、溶融スラグの特性
も安定する。
According to the refuse incineration ash melting treatment facility of the second aspect, the gas body is maintained at a temperature within a predetermined range by controlling the amount of oxygen or secondary air for secondary combustion. A stable high temperature can be obtained without being affected by the amount of residual combustibles in the incineration ash as in a melting furnace, and the characteristics of the molten slag are also stable.

【0058】請求項3記載のごみ焼却灰の溶融処理設備
によれば、焼却炉から排出された乾灰を高温のまま溶融
する方式であるために、熱効率が高く、別途処理すべき
高発熱ごみの燃焼熱を溶融に利用する有効利用法であ
り、電力使用量が少ない経済的な設備を提供することが
できる。また、高温の溶融装置ガスにさらされる部位は
溶融装置内のみであり、高熱対策を要する範囲が局限で
きるだけでなく、溶融装置ガスは、通常ごみ焼却炉側で
処理できるために、特別の排ガス処理装置を必要としな
い。さらに、高温空気加熱器等を使用しないために、金
属部の高温腐食が排除できるだけでなく、簡単な設備で
済むために故障の発生が少なく、万一の高温焼却炉側の
故障時、或いは休止時には、完全焼却を終えた焼却灰を
そのまま排出することができ、ごみ焼却施設全体の停止
にはつながらない。
According to the melting incineration ash melting treatment facility of claim 3, since the dry ash discharged from the incinerator is melted at a high temperature, the heat efficiency is high and the high heat-generating waste to be treated separately. This is an effective utilization method of utilizing the combustion heat of the above for melting, and it is possible to provide economical equipment with a small amount of power consumption. In addition, the area exposed to the high-temperature melting device gas is only in the melting device, and not only the range requiring high heat countermeasures can be limited, but since the melting device gas can be usually processed on the waste incinerator side, special exhaust gas treatment No equipment required. Furthermore, not using a high temperature air heater, etc. can eliminate high temperature corrosion of the metal part, and since it requires only simple equipment, there are few failures. At times, the incineration ash that has been completely incinerated can be discharged as it is, which does not lead to the shutdown of the entire refuse incineration facility.

【0059】請求項4記載のごみ焼却灰の溶融処理設備
によれば、高温焼却炉から排出される焼却灰を前記通常
ごみ焼却炉に搬入する搬出手段を設けたことで、不燃物
や落じん等も完全燃焼後、一括溶融処理が可能であり、
廃棄物による2次公害発生のおそれがない。
According to the waste incineration ash melting treatment facility of the fourth aspect, the incineration ash discharged from the high temperature incinerator is provided with the carry-out means for bringing the incinerator ash into the normal waste incinerator, so that incombustibles and dust are removed. After complete burning, etc., batch melting processing is possible,
There is no risk of secondary pollution from waste.

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

【図1】本発明に係るごみ焼却灰の溶融処理設備の概要
を示す断面図である。
FIG. 1 is a sectional view showing an outline of a melting incineration ash melting facility according to the present invention.

【図2】溶融装置周辺の概要を示す断面図である。FIG. 2 is a cross-sectional view showing an outline of the vicinity of a melting device.

【図3】本発明に係るごみ焼却灰の溶融処理設備の各物
質の概略の流れを示す説明図である。
FIG. 3 is an explanatory diagram showing a schematic flow of each substance of the melting incineration ash melting treatment facility according to the present invention.

【図4】本発明に係るごみ焼却灰の溶融処理設備の各物
質の概略の流れを示す一部拡大の説明図である。
FIG. 4 is a partially enlarged explanatory view showing a schematic flow of each substance of the melting incineration ash melting treatment facility according to the present invention.

【図5】溶融装置の他の形態を示す断面図である。FIG. 5 is a cross-sectional view showing another form of the melting device.

【図6】従来の直結形表面溶融炉の概要を示す図面であ
る。
FIG. 6 is a drawing showing an outline of a conventional direct-coupling type surface melting furnace.

【図7】従来の別置形プラズマ溶融炉の概要を示す図面
である。
FIG. 7 is a diagram showing an outline of a conventional separate plasma melting furnace.

【符号の説明】[Explanation of symbols]

1 通常ごみ焼却炉 3 溶融装置 4 高温焼却炉 46 2次燃焼室 54 焼却灰コンベア 55 灰コンベア 62 高温炉排ガス(未燃焼ガス) 63 溶融装置ガス 1 Normal refuse incinerator 3 Melting device 4 High temperature incinerator 46 Secondary combustion chamber 54 Incinerator ash conveyor 55 Ash conveyor 62 High temperature furnace exhaust gas (unburned gas) 63 Melting device gas

Claims (4)

【特許請求の範囲】[Claims] 【請求項1】 高発熱量の廃棄物を分別除去した通常ご
みを専焼する通常ごみ焼却炉と、高発熱量の廃棄物を専
焼する高温焼却炉とを併設し、高温焼却炉で発生する高
温のガス体の放射熱を利用し、通常ごみ焼却炉及び高温
焼却炉から排出される焼却灰を溶融処理することを特徴
とするごみ焼却灰の溶融処理方法。
1. A high temperature incinerator, which is equipped with a normal refuse incinerator that exclusively burns normal waste from which waste with high heat value is separated and removed and a high temperature incinerator that exclusively burns waste with high heat value. A method for melting waste incineration ash, which comprises melting the incineration ash discharged from a normal waste incinerator and a high-temperature incinerator by utilizing the radiant heat of the gas body.
【請求項2】 前記ガス体は、2次燃焼用の酸素または
2次空気量の制御により所定範囲の温度に保持すること
を特徴とする請求項1記載のごみ焼却灰の溶融処理方
法。
2. The method for melting waste incineration ash according to claim 1, wherein the gas body is maintained at a temperature within a predetermined range by controlling the amount of oxygen or secondary air for secondary combustion.
【請求項3】 高発熱量の廃棄物を分別除去した通常ご
みを専焼する通常ごみ焼却炉と、高発熱量の廃棄物を専
焼する高温焼却炉とを併設したごみ焼却灰の溶融処理設
備であって、 前記通常ごみ焼却炉の下流に溶融装置が設けられ、該溶
融装置の上方に前記高温焼却炉の2次燃焼室が設けられ
たことを特徴とするごみ焼却灰の溶融処理設備。
3. A waste incineration ash melting treatment facility equipped with an ordinary refuse incinerator that exclusively burns ordinary waste from which high-calorific value wastes have been separated and removed, and a high-temperature incinerator that exclusively burns high-calorific value wastes. There is provided a melting device provided downstream of the normal refuse incinerator, and a secondary combustion chamber of the high temperature incinerator is provided above the melting device.
【請求項4】 請求項3記載のごみ焼却灰の溶融処理設
備において、前記高温焼却炉から排出される焼却灰を前
記通常ごみ焼却炉に搬入する搬出手段が設けられたこと
を特徴とするごみ焼却灰の溶融処理設備。
4. The waste incineration ash melting treatment facility according to claim 3, further comprising: an unloading unit that carries incineration ash discharged from the high-temperature incinerator into the normal waste incinerator. Equipment for melting incineration ash.
JP17836795A 1995-07-14 1995-07-14 Method and equipment for melting incineration ash Expired - Fee Related JP2950754B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP17836795A JP2950754B2 (en) 1995-07-14 1995-07-14 Method and equipment for melting incineration ash

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP17836795A JP2950754B2 (en) 1995-07-14 1995-07-14 Method and equipment for melting incineration ash

Publications (2)

Publication Number Publication Date
JPH0926124A true JPH0926124A (en) 1997-01-28
JP2950754B2 JP2950754B2 (en) 1999-09-20

Family

ID=16047262

Family Applications (1)

Application Number Title Priority Date Filing Date
JP17836795A Expired - Fee Related JP2950754B2 (en) 1995-07-14 1995-07-14 Method and equipment for melting incineration ash

Country Status (1)

Country Link
JP (1) JP2950754B2 (en)

Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2000022348A1 (en) * 1998-10-12 2000-04-20 Nkk Corporation Waste disposal device
JP2000199620A (en) * 1998-10-12 2000-07-18 Nkk Corp Incinerating heat treating furnace for refuse
JP2001021129A (en) * 1999-07-06 2001-01-26 Plantec Inc Direct connected ignition ash melting facility and operation control method
KR100651271B1 (en) * 2006-04-14 2006-11-30 한국기계연구원 Waste pyrolysis and smelting system
WO2012130554A1 (en) * 2011-03-25 2012-10-04 Clyde Bergemann Drycon Gmbh Incinerator having afterburner grate

Cited By (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2000022348A1 (en) * 1998-10-12 2000-04-20 Nkk Corporation Waste disposal device
JP2000199620A (en) * 1998-10-12 2000-07-18 Nkk Corp Incinerating heat treating furnace for refuse
JP2001021129A (en) * 1999-07-06 2001-01-26 Plantec Inc Direct connected ignition ash melting facility and operation control method
KR100651271B1 (en) * 2006-04-14 2006-11-30 한국기계연구원 Waste pyrolysis and smelting system
WO2012130554A1 (en) * 2011-03-25 2012-10-04 Clyde Bergemann Drycon Gmbh Incinerator having afterburner grate
CN103492807A (en) * 2011-03-25 2014-01-01 克莱德贝尔格曼干控制有限公司 Incinerator having afterburner grate

Also Published As

Publication number Publication date
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