JPH0611124A - Waste melting furnace and waste feeding method - Google Patents

Waste melting furnace and waste feeding method

Info

Publication number
JPH0611124A
JPH0611124A JP5060672A JP6067293A JPH0611124A JP H0611124 A JPH0611124 A JP H0611124A JP 5060672 A JP5060672 A JP 5060672A JP 6067293 A JP6067293 A JP 6067293A JP H0611124 A JPH0611124 A JP H0611124A
Authority
JP
Japan
Prior art keywords
waste
combustion space
melting furnace
combustion
filling layer
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
JP5060672A
Other languages
Japanese (ja)
Other versions
JP3081402B2 (en
Inventor
Takeshi Tsunemi
武志 常深
Takeshi Fujii
岳 藤井
Muneharu Ichikawa
宗春 市川
Makoto Shimizu
信 清水
Tetsuo Horie
徹男 堀江
Harunobu Sakabe
治信 坂部
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
IHI Corp
Osaka Gas Co Ltd
Original Assignee
IHI Corp
Osaka Gas Co Ltd
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by IHI Corp, Osaka Gas Co Ltd filed Critical IHI Corp
Priority to JP05060672A priority Critical patent/JP3081402B2/en
Publication of JPH0611124A publication Critical patent/JPH0611124A/en
Application granted granted Critical
Publication of JP3081402B2 publication Critical patent/JP3081402B2/en
Anticipated expiration legal-status Critical
Expired - Fee Related legal-status Critical Current

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

Abstract

PURPOSE:To suppress the generation of dispersing dust and to uniform temp. in a furnace by a method wherein a droop wall protruded downward from the upper part side of a combustion space is provided in a boundary position between a combustion space and a filled layer. CONSTITUTION:A lowering guide surface 8a being a slope which is protruded downward from the upper part side of a combustion space 4 positioned more upward on the combustion space 4 side with the increase of separation of it from a coke-filled layer 2 is formed in a boundary position between the combustion space 4 and a coke-filled layer 2. A droop wall 8 made of refractories having the lowering guide surface is provided. Thus, combustion gas in the combustion space 4 is further delayed in an advection current to the interior of the coke-filled layer 2 compared with a case having no droop wall 8, and the flow direction of combustion gas to the interior of the coke-filled layer 2 is set to an oblique down direction. This method uniformizes temperature distribution in sectional direction of the interior of the filled layer and reduces dispersion of dust.

Description

【発明の詳細な説明】Detailed Description of the Invention

【0001】[0001]

【産業上の利用分野】本発明は、コークス等の炭素系可
燃物で形成した充填層に粉末状で汚泥等の廃棄物を吹込
むことにより、廃棄物を燃焼するとともに溶融スラグ化
する場合に、処理に伴って発生するダストの飛散防止と
燃費低減を目的として提案されている廃棄物溶融炉に関
するものであり、さらに詳細には、炭素系可燃物質で形
成される充填層を備え、充填層の上面よりも低い位置で
充填層の横断方向の外周部に、充填層に連通する環状の
燃焼空間を備え、燃焼空間に廃棄物を粉末状で吹き込ん
で、燃焼空間及び充填層において、廃棄物を燃焼させる
とともに溶融スラグ化する廃棄物溶融炉および、この廃
棄物溶融炉への廃棄物の供給方法に関する。
BACKGROUND OF THE INVENTION The present invention relates to a case where powdered waste such as sludge is blown into a packed bed formed of a carbon-based combustible material such as coke to burn the waste and form molten slag. The present invention relates to a waste melting furnace proposed for the purpose of preventing the scattering of dust generated during processing and reducing fuel consumption. More specifically, the present invention relates to a waste melting furnace, which includes a packing layer formed of a carbon-based combustible substance. An annular combustion space communicating with the packed bed is provided in the outer peripheral portion of the packed bed at a position lower than the upper surface of the, and the waste is blown into the combustion space in the form of powder to generate waste in the combustion space and the packed bed. TECHNICAL FIELD The present invention relates to a waste melting furnace that burns fuel and turns it into molten slag, and a method of supplying waste to the waste melting furnace.

【0002】[0002]

【従来の技術】粉末状で汚泥等の廃棄物を高温炉床に吹
込み燃焼・溶融する場合、充填層への直接吹込みをおこ
なおうとすると、コークス表面への廃棄物(汚泥)付着
による燃焼阻害、有機分の分解による吸熱現象等により
充填層の温度低下を招くこととなる。結果、炉に於ける
廃棄物ダストによる閉塞が進み、炉の操業悪化を起こす
こととなる。そこで、図3(ロ)に示すように、これら
弊害を除くために人為的に充填層の周部に環状の燃焼空
間を設け、この燃焼空間から充填層に向かって横方向に
燃焼ガスを送り出して、上記廃棄物を燃焼・溶融処理す
る方法が考えられている(特願平2−131746
号)。
2. Description of the Related Art When powder-like waste such as sludge is blown into a high-temperature hearth for combustion and melting, if direct blown into the packed bed, the waste (sludge) will adhere to the surface of the coke. The temperature of the packed bed is lowered due to combustion inhibition, endothermic phenomenon due to decomposition of organic components, and the like. As a result, clogging by waste dust in the furnace progresses, and the operation of the furnace deteriorates. Therefore, as shown in FIG. 3B, in order to eliminate these adverse effects, an annular combustion space is artificially provided in the peripheral portion of the packed bed, and the combustion gas is sent laterally from this combustion space toward the packed bed. Then, a method of burning and melting the above waste has been considered (Japanese Patent Application No. 2-131746).
issue).

【0003】[0003]

【発明が解決しようとする課題】しかし、前記構成によ
れば吹込まれた廃棄物粉末は、燃焼空間で燃焼後、溶融
又はチャー化し、コークス層で溶融スラグ化し出滓口よ
り排出されるはずであるが、実際にはコークス層に捕集
されず、排ガス中へダストとして飛散される場合があ
る。さらに、こういった燃焼・溶融構造においては、充
填層内における周辺流が多いため周辺壁ぎわのみが高温
となる。この理由は、通常の充填層構造における“周辺
流化現象”によるものと考えられる。すなわち、充填層
構造では羽口より吹込まれたガスは炉の中心部より周辺
の壁ぎわを流れやすく、製鉄用の高炉においては周辺風
速は中心風速の2倍以上になるといわれている。この現
象は本願のように充填層構造が薄い場合、より顕著とな
る。結果、吹込まれた粉末状廃棄物は壁ぎわより吹抜け
排ガス中に飛散するものと考えられ、また、炉中心への
ガス流れが少ないことから炉中心の温度も充分高温化せ
ず炉内温度分布は不均一にならざるを得ない。
However, according to the above-mentioned structure, the waste powder blown in should be melted or turned into char after burning in the combustion space and turned into molten slag in the coke layer and discharged from the outlet. However, in some cases, they are not actually collected in the coke layer and may be scattered as dust in the exhaust gas. Further, in such a combustion / melting structure, since there are many peripheral flows in the packed bed, only the peripheral wall wrinkles become high in temperature. The reason for this is considered to be "peripheral fluidization phenomenon" in the normal packed bed structure. That is, in the packed bed structure, the gas blown from the tuyere easily flows through the wall around the center of the furnace, and in the blast furnace for iron making, the peripheral wind speed is said to be more than twice the central wind speed. This phenomenon becomes more remarkable when the filling layer structure is thin as in the present application. As a result, it is considered that the powdered waste that was blown in is scattered in the exhaust gas that passes through the walls and that the temperature of the furnace center does not rise sufficiently because the gas flow to the furnace center is low. Has to be non-uniform.

【0004】その結果、このような廃棄物溶融炉におい
ては、以下のような問題が発生する場合がある。 1.ダスト飛散(粉末状廃棄物のショートパス) 2.炉内温度の不均一による充填層内のブリッヂ形成 3.周辺コークスの部分燃焼、粉末状廃棄物の未燃飛散
による、コークス消費量の増加 4.炉操業不安定による出滓不良
As a result, the following problems may occur in such a waste melting furnace. 1. Dust scattering (short path for powder waste) 2. Bridge formation in packed bed due to uneven temperature in the furnace. 3. Increase in coke consumption due to partial combustion of peripheral coke and unburned powder waste. Poor slag due to unstable furnace operation

【0005】従って、本発明の目的は、飛散するダスト
の発生をできるだけ抑制することができ、炉内温度が均
一で、廃棄物の処理効率が高い廃棄物溶融炉を得るとと
もに、この目的を良好に達成できる廃棄物の供給方法を
得ることにある。
Therefore, an object of the present invention is to obtain a waste melting furnace in which the generation of scattered dust can be suppressed as much as possible, the temperature inside the furnace is uniform, and the disposal efficiency of waste is high, and at the same time, this object is improved. To obtain a waste supply method that can be achieved.

【0006】[0006]

【課題を解決するための手段】この目的を達成するため
の本願第一の発明による廃棄物溶融炉の特徴構成は、燃
焼空間と充填層の境界位置に、燃焼空間の上部側より下
方に張り出した下垂壁を備えたことにあり、さらに、本
願第二の発明による廃棄物溶融炉の特徴構成は、燃焼室
より充填層へ移流する燃焼ガスの流れ方向が、斜め下向
きに設定されていることにある。さらに、前記第一、第
二発明の構成においては、周方向に分散した複数の導入
部位から廃棄物を燃焼空間に供給する供給手段が備えら
れ、供給手段による廃棄物の供給方向が、環状の燃焼空
間に旋回流を形成する向きに設定されていることが好ま
しい。そして、このような構成の廃棄物溶融炉におい
て、廃棄物の供給方法として、複数の導入部位におい
て、燃焼空間の周方向で順次、廃棄物供給、廃棄物供給
停止を行い、燃焼空間に形成される旋回流の旋回を促進
もしくは抑制制御することが好ましい。そして、それら
の作用・効果は次の通りである。
To achieve this object, the waste melting furnace according to the first aspect of the present invention is characterized in that it is projected downward from the upper side of the combustion space at the boundary position between the combustion space and the packed bed. In addition, the waste melting furnace according to the second aspect of the present invention is characterized in that the flow direction of the combustion gas advancing from the combustion chamber to the packed bed is set obliquely downward. It is in. Further, in the configurations of the first and second inventions, a supply means for supplying the waste to the combustion space from a plurality of introduction sites dispersed in the circumferential direction is provided, and the supply direction of the waste by the supply means is an annular shape. It is preferable that the combustion space is set so as to form a swirling flow. Then, in the waste melting furnace of such a configuration, as a waste supply method, waste is sequentially supplied in the circumferential direction of the combustion space at a plurality of introduction sites, and the waste supply is stopped to form in the combustion space. It is preferable to accelerate or suppress the swirling of the swirling flow. The actions and effects thereof are as follows.

【0007】[0007]

【作用】先ず第一、第二の構成の廃棄物溶融炉において
は、下垂壁を設けることにより、或いは燃焼ガスの流れ
方向を制御することにより、燃焼室へ吹込まれた粉末状
廃棄物は下方に向けられ、充填層内部に浸入する。そし
て、充填層中央側での燃焼処理が促進され、充填層内で
の、その横断方向の温度分布が均一化される。又、燃焼
処理される廃棄物量が増加(ダスト飛散が減少する)
し、結果的に処理温度も上昇する。従って、従来のよう
にショートパスを起こして、廃棄物が燃焼空間から充填
層側壁近傍部を上昇する壁側吹抜けが防止される。一
方、環状の燃焼空間内の燃焼ガスは、この空間内におい
て充填層周りに旋回軌跡を描きながら充填層内に送りこ
まれることとなるが、下垂壁もしくは、これに相当する
流れ方向の制御により、燃焼空間での滞留時間を充分と
ることが可能となり、廃棄物のこの空間内での処理が従
来よりも促進される。結果、本願の廃棄物溶融炉におい
ては、可燃分の完全燃焼と燃焼による昇温が達成でき、
炉を所定の温度に容易に維持できるとともに、操業も安
定して行える。ここで、廃棄物の導入部位を一箇所に限
定する場合は、吹き込み部(導入部位)の耐火物の部分
磨耗により燃焼空間形態等の不均一化が起こる場合もあ
る。このような不均一化が発生すると、燃焼の不均一、
溶融能力の低下等を誘起する場合もある。従って、吹き
込み箇所を環状の燃焼空間の周方向で複数個設け、分散
させる構成が好ましい。さらに、廃棄物の供給に当たっ
て供給手段を作動させる場合に、各導入部位において廃
棄物の供給順、供給タイミング等を制御する場合は、燃
焼空間に形成される旋回流の状態を容易に制御できる。
そして、燃焼空間における廃棄物の昇温、乾燥処理を促
進したり、抑制したりして、この部位の処理状態を炉全
体の操業状況に則したものとすることができ、全体とし
て良好に処理を継続できる。
First, in the waste melting furnace of the first and second configurations, the powdery waste blown into the combustion chamber is lowered by providing the hanging wall or controlling the flow direction of the combustion gas. And penetrates inside the packed bed. Then, the combustion treatment on the central side of the packed bed is promoted, and the temperature distribution in the transverse direction in the packed bed is made uniform. In addition, the amount of waste processed by combustion increases (dust scattering decreases)
As a result, the processing temperature also rises. Therefore, it is possible to prevent the wall side blow-through in which the waste material is short-circuited and rises from the combustion space to the vicinity of the side wall of the packed bed as in the conventional case. On the other hand, the combustion gas in the annular combustion space will be sent into the packed bed while drawing a swirling locus around the packed bed in this space, but depending on the drooping wall or the control of the flow direction corresponding to this, A sufficient residence time in the combustion space can be taken, and the treatment of waste in this space is promoted more than before. As a result, in the waste melting furnace of the present application, complete combustion of combustibles and temperature rise due to combustion can be achieved,
The furnace can be easily maintained at a predetermined temperature and the operation can be performed stably. Here, when the waste introduction site is limited to one place, non-uniformity of the combustion space form or the like may occur due to partial wear of the refractory material at the blow-in portion (introduction site). When such non-uniformity occurs, the non-uniformity of combustion,
In some cases, a decrease in melting ability may be induced. Therefore, it is preferable that a plurality of blow-in points are provided in the circumferential direction of the annular combustion space to be dispersed. Further, when the supply means is operated in supplying the waste, when controlling the supply order, supply timing, etc. of the waste at each introduction site, the state of the swirling flow formed in the combustion space can be easily controlled.
Then, by promoting or suppressing the temperature rise and drying process of the waste in the combustion space, it is possible to make the processing state of this part in line with the operating conditions of the entire furnace, and the overall good processing is performed. Can continue.

【0008】[0008]

【発明の効果】従って、本願の廃棄物溶融炉において
は、廃棄物のショートパスが防止できる結果、廃棄物の
ダスト飛散量が減少する。更に、燃焼室内での燃焼が促
進され温度が高温になるとともに、炉内充填層温度の均
一化が達成され操業が安定した。上記のような諸要因か
ら、廃棄物の高温部での部分溶融や低温部でのダスト付
着によるブリッヂの発生が防止できるとともに、廃棄物
処理に伴う充填層を構成する材料である炭素系可燃物質
(例えばコークス)の燃費低減が図れた。さらに、独特
の供給構成を採用することにより、燃焼空間に於ける燃
焼を安定したものとすることができ、さらに、この空間
に於ける燃焼状態をも容易に制御できるようになった。
As described above, in the waste melting furnace of the present invention, the short path of the waste can be prevented, and as a result, the amount of dust scattering of the waste is reduced. Further, the combustion in the combustion chamber was promoted and the temperature became high, and the temperature of the packed bed in the furnace was made uniform and the operation was stabilized. Due to the various factors mentioned above, carbon-based combustible substances, which are materials that can prevent the generation of bridges due to partial melting of waste in the high temperature part and dust adhesion in the low temperature part, and that constitute the packed bed accompanying waste disposal The fuel consumption of (for example, coke) was reduced. Furthermore, by adopting a unique supply configuration, combustion in the combustion space can be made stable, and the combustion state in this space can be easily controlled.

【0009】[0009]

【実施例】本願の実施例を図面に基づいて説明する。図
1には、廃棄物溶融炉1の充填層であるコークス充填層
2近傍の断面図が示されている。図示するように、この
廃棄物溶融炉1は、概略縦型円筒形状のコークス充填層
2を備えており、このコークス充填層2には、その下部
位置に溶融スラグが出滓される出滓口3が備えられると
ともに、このコークス充填層2の上面よりも低い位置で
その横断方向外周部に、環状の燃焼空間4を備え、さら
に、このコークス充填層2の上部部位にフリーボード5
を備えて構成されている。そして、このコークス充填層
2に対して、これに一次空気を供給する一次空気供給ノ
ズル6と、前記フリーボード5の入口近傍位置に、この
部位に二次空気を供給する二次空気供給ノズル7とが備
えられている。
Embodiments of the present application will be described with reference to the drawings. FIG. 1 shows a cross-sectional view in the vicinity of a coke packed bed 2 which is a packed bed of the waste melting furnace 1. As shown in the figure, the waste melting furnace 1 is provided with a coke packing layer 2 having a substantially vertical cylindrical shape, and the coke packing layer 2 has a slag port through which molten slag is slagged at a lower position thereof. 3 is provided, and an annular combustion space 4 is provided at a position lower than the upper surface of the coke packed layer 2 at an outer peripheral portion in the transverse direction thereof, and a freeboard 5 is provided at an upper portion of the coke packed layer 2.
It is configured with. A primary air supply nozzle 6 for supplying primary air to the coke-filled layer 2 and a secondary air supply nozzle 7 for supplying secondary air to this portion near the inlet of the freeboard 5 are provided. And are provided.

【0010】次に、前記燃焼空間4について説明する
と、この燃焼空間4に対して、これに、廃棄物である汚
泥を粉末状で搬送空気により供給する廃棄物供給ノズル
4a、酸素含有ガスを吹込む酸素含有ガス供給ノズル4
b、補助燃料を吹き込む補助燃料吹き込みノズル4cが
備えられている。従って、この燃焼空間4においては、
燃料の燃焼が起こっているとともに、この燃焼空間4に
送りこまれてくる粉末状の汚泥は、乾燥され、燃焼さ
れ、発生する燃焼ガスが、未燃物とともにコークス充填
層2周りに旋回した軌跡を描きながらコークス充填層2
内に送り込まれる。
Next, the combustion space 4 will be described. To the combustion space 4, a waste supply nozzle 4a for supplying sludge, which is a waste in powder form, by carrier air, and an oxygen-containing gas are blown. Oxygen-containing gas supply nozzle 4
b, an auxiliary fuel injection nozzle 4c for injecting auxiliary fuel is provided. Therefore, in this combustion space 4,
While the fuel is burning, the powdery sludge sent into the combustion space 4 is dried and burned, and the generated combustion gas swirls around the coke packed layer 2 along with unburned matter. Coke filling layer 2 while drawing
Sent in.

【0011】さらに、燃焼空間4とコークス充填層2の
境界位置に、燃焼空間4の上部側より下方に張り出し、
燃焼空間4側でコークス充填層2から離間するに伴って
上方に位置する傾斜面である下降案内面8aを備えた、
耐火物製の下垂壁8が備えられている。従って、本願の
廃棄物溶融炉1においては、この下垂壁8を備えること
により、燃焼空間4内の燃焼ガスは、この下垂壁8を備
えない場合と比較して、コーク充填層2内への移流が遅
れる(旋回量が増加する)とともに、コークス充填層2
内への燃焼ガスの流れ方向が、斜め下向きに設定される
こととなる。
Further, at the boundary position between the combustion space 4 and the coke packed layer 2, the lower side of the combustion space 4 is projected downward.
A downward guide surface 8a, which is an inclined surface located upward as it is separated from the coke filling layer 2 on the combustion space 4 side,
A hanging wall 8 made of refractory is provided. Therefore, in the waste melting furnace 1 of the present application, by providing the hanging wall 8, the combustion gas in the combustion space 4 enters the coke filling layer 2 as compared with the case where the hanging wall 8 is not provided. The advection is delayed (the swirling amount increases) and the coke packed bed 2
The flow direction of the combustion gas inward is set to be obliquely downward.

【0012】さらに、燃焼空間4への廃棄物である汚
泥、酸素含有ガス、補助燃料の供給構造について説明す
る。図2に、この燃焼空間4位置におけるの横断面図が
示されている。図示するように、前述の廃棄物供給ノズ
ル4a、酸素含有ガス供給ノズル4b、補助燃料吹き込
みノズル4c(後者の二者は単一のノズルが共用されて
いる)を備えた供給装置40が、環状の燃焼空間4の周
りに均等に4箇所、分散配置されており、これらの吹き
込み方向がそれぞれ環状の燃焼空間4の接線方向に設定
されている。結果、供給装置40より供給される空気搬
送状態の汚泥、酸素含有ガス、補助燃料は、燃焼空間4
に一定方向(図示する例においては時計方向)の旋回流
Fを構成する。さて、これら供給装置40に対して制御
装置41が備えられており、各供給装置40における供
給物(汚泥、酸素含有ガス、補助燃料ガス)の供給、供
給停止制御、あるいは供給量制御をおこなう構成が採用
されている。供給、供給停止制御に関しては、各供給装
置40における吹き込みタイミングを制御することによ
り、燃焼空間4に形成される旋回流の旋回を促進もしく
は抑制制御できる。即ち、旋回を促進したい場合は、周
方向に沿った各供給装置40からの吹き込みタイミング
を順次、早くするのであり、旋回を抑制したい場合は、
吹き込みを一部の供給装置40に限定するとともに、吹
き込み速度を遅らせる等の操作をおこなうことにより、
この制御をおこなうことが可能となる。このような制御
は、各供給装置40による供給量調節でも可能である。
従って、燃焼空間4、充填層2内での燃焼状況に応じ
て、燃焼空間4での処理を制御して、炉全体の操業状態
を良く制御された安定したものとすることができる。
Further, the supply structure of sludge, oxygen-containing gas and auxiliary fuel, which are wastes, to the combustion space 4 will be described. FIG. 2 shows a cross-sectional view of the combustion space 4 at the position. As shown in the figure, the supply device 40 equipped with the waste supply nozzle 4a, the oxygen-containing gas supply nozzle 4b, and the auxiliary fuel injection nozzle 4c (the latter two have a single nozzle in common) has an annular shape. 4 are evenly distributed around the combustion space 4 and the blowing directions thereof are respectively set to the tangential direction of the annular combustion space 4. As a result, the sludge in the air-carrying state, the oxygen-containing gas, and the auxiliary fuel supplied from the supply device 40 are transferred to the combustion space
To form a swirling flow F in a fixed direction (clockwise in the illustrated example). Now, a control device 41 is provided for these supply devices 40, and the supply (supply of sludge, oxygen-containing gas, auxiliary fuel gas) in each supply device 40, supply stop control, or supply amount control is performed. Has been adopted. Regarding the supply and supply stop control, by controlling the blowing timing in each supply device 40, the swirling of the swirling flow formed in the combustion space 4 can be accelerated or suppressed. That is, when it is desired to accelerate the turning, the blowing timings from the respective supply devices 40 along the circumferential direction are sequentially advanced, and when the turning is to be suppressed,
By limiting the blowing to a part of the supply device 40 and performing operations such as slowing the blowing speed,
This control can be performed. Such control can also be performed by adjusting the supply amount by each supply device 40.
Therefore, the processing in the combustion space 4 can be controlled according to the combustion conditions in the combustion space 4 and the packed bed 2 to make the operating condition of the entire furnace stable and well controlled.

【0013】さらに、夫々の供給装置40は、粉末状の
汚泥を対応する導入部位42に導く第一導入路43a
と、第一導入路43aの周部に形成され且つ酸素含有ガ
スもしくはこれと燃料ガスの混合した混合ガスを前記導
入部位42の近傍に導く第二導入路43bとを備えて構
成されている。そして、直線状の第一、第二導入路43
a、43bに対して、酸素含有ガスもしくは混合ガス
は、第二導入路43bの基端側で、この導入路43bに
直交する方向から供給され、この環状流路を螺旋軌跡を
描きながら流れる構成が採用されている。従って、各ノ
ズル4a,4b,4cの先端側に位置する各導入部位4
2においては、酸素含有ガスもしくは混合ガスが汚泥搬
送流の周りで螺旋状の旋回流として供給される。よっ
て、燃焼空間4内での汚泥、酸素含有ガス(燃料ガスを
含む場合もある)は有効に、拡散、混合される。以上の
説明において、燃焼空間4に対して、この空間の周方向
に分散した複数の導入部位42に、少なくとも廃棄物を
供給する系を、供給手段と称する。さらに、第二導入路
43b内に酸素含有ガス(燃料ガスを含む場合もある)
の螺旋渦流を形成する系を旋回供給手段と称する。
Further, each of the supply devices 40 has a first introduction path 43a for guiding the powdery sludge to the corresponding introduction site 42.
And a second introduction passage 43b which is formed in the peripheral portion of the first introduction passage 43a and guides the oxygen-containing gas or a mixed gas of the oxygen-containing gas and the fuel gas to the vicinity of the introduction portion 42. Then, the linear first and second introduction paths 43
In contrast to a and 43b, the oxygen-containing gas or the mixed gas is supplied at the base end side of the second introduction passage 43b from the direction orthogonal to the introduction passage 43b, and flows in the annular passage while drawing a spiral locus. Has been adopted. Therefore, the introduction portions 4 located on the tip side of the nozzles 4a, 4b, 4c
In 2, the oxygen-containing gas or mixed gas is supplied as a spiral swirl flow around the sludge carrier flow. Therefore, sludge and oxygen-containing gas (which may include fuel gas) in the combustion space 4 are effectively diffused and mixed. In the above description, a system for supplying at least waste to the combustion space 4 at the plurality of introduction sites 42 dispersed in the circumferential direction of the space is referred to as a supply means. Further, an oxygen-containing gas (which may include a fuel gas) in the second introduction passage 43b.
The system that forms the spiral vortex flow is referred to as swirl supply means.

【0014】以下、本願の廃棄物溶融炉1の働きについ
て説明する。コークス充填層2は充填層下部にある一時
空気吹込みノズル6より吹込まれた予熱された酸素含有
ガスとしての一次空気により燃焼され1500〜160
0℃の高温に保持される。一方粉末状の廃棄物、例えば
汚泥等は乾燥後約10%水分の状態で燃焼空間に設けら
れた廃棄物供給ノズル4aより燃焼空間4に吹込まれ、
乾燥、燃焼、溶融されるとともに、コークス充填層2内
に送られて、未燃分もコークス充填層2で溶融されスラ
グとされ、出滓口3より排出される。ここで、燃焼溶融
をスムーズに行わせるためには、燃焼空間温度は120
0℃以上、コークス充填層温度は1400〜1500℃
以上に維持する必要があるのであるが、本願の廃棄物溶
融炉1においては、下垂壁8を設けることにより、燃焼
空間4室へ吹込まれた粉末状廃棄物及び酸素含有ガスは
下方に向けられコークス充填層2内部に浸入され、ショ
ートパスによる壁側吹抜けが防止できること等の理由か
ら、良好な操業状態が得られる。即ち、燃焼空間4での
滞留時間も充分となり、可燃分の完全燃焼と燃焼による
昇温が達成され、炉を所定の温度に維持でき、操業も安
定に行える。一方、従来技術のように、下垂壁8がない
場合は、粉末状ダストの燃焼空間内燃焼が充分おこなわ
れ難いため、廃棄物である汚泥等はダストとしてそのま
ま排ガスに飛散する。
The operation of the waste melting furnace 1 of the present application will be described below. The coke packed bed 2 is burned by the primary air as a preheated oxygen-containing gas blown from the temporary air blowing nozzle 6 located below the packed bed 1500 to 160.
It is kept at a high temperature of 0 ° C. On the other hand, powdery waste such as sludge is blown into the combustion space 4 from the waste supply nozzle 4a provided in the combustion space in a state of about 10% water content after drying.
While being dried, burned and melted, it is sent into the coke filling layer 2 and unburned components are also melted in the coke filling layer 2 to form slag, which is discharged from the outlet 3. Here, in order to smoothly perform the combustion melting, the combustion space temperature is 120
0 ° C or higher, coke packed bed temperature is 1400 to 1500 ° C
It is necessary to maintain the above, but in the waste melting furnace 1 of the present application, by providing the hanging wall 8, the powdery waste and the oxygen-containing gas blown into the combustion space 4 chamber are directed downward. A good operating condition can be obtained because, for example, it can be prevented from being blown into the coke filling layer 2 to prevent wall side blow-through due to a short pass. That is, the residence time in the combustion space 4 becomes sufficient, complete combustion of combustible components and temperature rise by combustion are achieved, the furnace can be maintained at a predetermined temperature, and stable operation can be performed. On the other hand, as in the prior art, when the hanging wall 8 is not provided, it is difficult to sufficiently combust the powdery dust in the combustion space, and thus sludge as waste is scattered as dust into the exhaust gas as it is.

【0015】以下に、本願の発明の有用性に関する実験
データを図3とともに説明する。図3(イ)は、下垂壁
8を備えた構成の廃棄物溶融炉1の炉内温度分布を模式
的に示したものであり、図3(ロ)に示すものは下垂壁
を備えない従来型の廃棄物溶融炉のものである。夫々の
運転状況を以下に示す。 運転状況比較 テスト結果 下垂壁有り 下垂壁無し 汚泥吹込み量 kg/h 30 30 コークス量 kg/h 12 20 ダスト飛散量 g/Nm3 2.2 6 1次空気量 Nm3 /h 62 70 燃焼空間吹込み空気 Nm3 /h 60 90 以上の結果から明らかなように、下垂壁8を設けた場合
は、炉内温度の上昇、及び均一化が達成されるととも
に、同一の汚泥の処理に要するコークス量の大幅な減量
が達成され、ダスト飛散量も大幅に減少する。
Experimental data relating to the usefulness of the present invention will be described below with reference to FIG. FIG. 3 (A) schematically shows the temperature distribution in the furnace of the waste melting furnace 1 having the structure including the hanging wall 8, and the one shown in FIG. 3 (B) is a conventional one without the hanging wall. Type of waste melting furnace. The operation status of each is shown below. Operation status comparison Test results With hanging wall Without hanging wall Sludge injection amount kg / h 30 30 Coke amount kg / h 12 20 Dust scattering amount g / Nm 3 2.2 6 Primary air amount Nm 3 / h 62 70 Combustion space Blow-in air Nm 3 / h 60 90 As is apparent from the above results, when the hanging wall 8 is provided, the temperature inside the furnace is increased and the temperature is made uniform, and coke required for treating the same sludge is obtained. A significant reduction in the amount is achieved, and the amount of dust scattering is also greatly reduced.

【0016】本願の廃棄物溶融炉の構成・作用は以上説
明したとおりであるが、出来る限り粉末状の廃棄物の周
辺壁ぎわでのダスト吹抜けを防ぎ層内へ送り込むため、
一般の溶融炉ではコークス充填層2を形成する場合に、
コークスを周辺部に厚く、中心部に薄くするような操
作、いわゆるコークスの層構造を変えることにより炉内
の流れを制御することも考えられるが、これは本願にお
いてはコークス充填層の厚みが薄いことから採用不可能
である。さらに、粉末状の廃棄物を炉中央側は送り込む
ために燃焼空間への吹き込み速度を上昇させると、充填
層の流動化が同様の理由から発生することとなるため、
この対策も採用できない。従って、本願においては、燃
焼空間4とコークス充填層2の間に下垂壁8を設け、燃
焼空間4に吹込まれた空気と粉末状の廃棄物がショート
パスして直ちに壁ぎわからフリーボード5に吹抜けるこ
とを防止しすることにより、上記のような顕著な効果を
得ることができた。
The structure and operation of the waste melting furnace of the present application are as described above, but in order to prevent dust blow-through at the peripheral wall of the powdery waste as much as possible and send it into the layer,
In the case of forming the coke filling layer 2 in a general melting furnace,
It is also possible to control the flow in the furnace by changing the so-called coke layer structure, such as making the coke thick in the peripheral portion and thin in the central portion, but in the present application, this is because the thickness of the coke packed layer is thin. Therefore, it cannot be adopted. Furthermore, if the blowing speed into the combustion space is increased in order to send the powdery waste to the center side of the furnace, fluidization of the packed bed will occur for the same reason.
This measure cannot be adopted either. Therefore, in the present application, the hanging wall 8 is provided between the combustion space 4 and the coke packed layer 2, and the air and the powdery waste blown into the combustion space 4 short pass to the freeboard 5 immediately from the wall edge. By preventing blow-through, the above remarkable effects could be obtained.

【0017】〔別実施例〕上記の実施例においては、下
垂壁を縦断面視、下方向に張り出した三角形状のものと
したが、これは単なる下方に延出された縦断面視方形の
壁面としてもよい。要するに、燃焼空間4からコークス
充填層2内に導かれるガスが、コークス充填層2の側部
に直接移動し、燃焼されることなく、充填層を貫通して
排出されるのを回避できる構成であれば、いかなる構成
でもよい。さらに、この下垂壁8を実施例に示すよう
に、内部が充填された耐火物で構成するのみならず、中
空構造とし、この部位を水冷構造、ボイラー構造等によ
り構成してもよい。
[Other Embodiments] In the above embodiments, the hanging wall has a triangular shape that projects downward in a vertical sectional view, but this is a mere downwardly extending rectangular wall surface in vertical sectional view. May be In short, the gas guided from the combustion space 4 into the coke packed bed 2 moves directly to the side of the coke packed bed 2 and is prevented from being burnt and discharged through the packed bed. Any configuration may be used as long as it is provided. Further, as shown in the embodiment, the hanging wall 8 is not limited to a refractory having the inside filled, but may have a hollow structure, and this portion may have a water cooling structure, a boiler structure, or the like.

【0018】又、実施例ではコークスを使用する例を示
したが、これは炭素系可燃物質であればいかなるもので
もよい。
Further, although an example using coke was shown in the embodiment, any carbon-based combustible substance may be used.

【0019】処理対象物としては、汚泥の他、都市ご
み、各種産業廃棄物、又それらを脱水乾燥、焼却、破砕
処理等して得られた中間処理物等が対象となり、粉末状
で燃焼空間に吹き込めるものであれば、いかなるものも
対象となる。尚、特許請求の範囲の項に図面との対照を
便利にするために符号を記すが、該記入により本発明は
添付図面の構成に限定されるものではない。
In addition to sludge, municipal solid waste, various industrial wastes, and intermediate processed products obtained by dewatering, drying, incinerating, crushing, and the like of sludge, as the object to be treated, are powdered in a combustion space. Anything that can be blown into It should be noted that reference numerals are added to the claims for convenience of comparison with the drawings, but the present invention is not limited to the configurations of the accompanying drawings by the entry.

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

【図1】廃棄物溶融炉の構成を示す図FIG. 1 is a diagram showing the structure of a waste melting furnace.

【図2】燃焼空間位置に於ける廃棄物溶融炉の横断面図FIG. 2 is a cross-sectional view of the waste melting furnace in the combustion space position.

【図3】炉内温度の比較結果を示す図FIG. 3 is a diagram showing a comparison result of furnace temperatures.

【符号の説明】[Explanation of symbols]

1 廃棄物溶融炉 2 充填層 4 燃焼空間 8 下垂壁 42 導入部位 43a 第一導入路 43b 第二導入路 F 旋回流 1 Waste Melting Furnace 2 Packed Bed 4 Combustion Space 8 Hanging Wall 42 Introduction Site 43a First Introduction Path 43b Second Introduction Path F Swirling Flow

───────────────────────────────────────────────────── フロントページの続き (72)発明者 市川 宗春 大阪府大阪市東成区中道1丁目4番2号 大阪ガスエンジニアリング株式会社内 (72)発明者 清水 信 東京都千代田区大手町二丁目2番1号 石 川島播磨重工業株式会社内 (72)発明者 堀江 徹男 東京都千代田区大手町二丁目2番1号 石 川島播磨重工業株式会社内 (72)発明者 坂部 治信 東京都千代田区大手町二丁目2番1号 石 川島播磨重工業株式会社内 ─────────────────────────────────────────────────── ─── Continuation of the front page (72) Inventor Muneharu Ichikawa 1-2-4 Nakamichi, Higashinari-ku, Osaka City, Osaka Prefecture (72) Inventor Shin Shimizu 2-chome, Otemachi 2-chome, Chiyoda-ku, Tokyo No. 1 Ishi Kawashima Harima Heavy Industries Co., Ltd. (72) Inventor Tetsuo Horie 22-1 Otemachi 2-chome, Chiyoda-ku, Tokyo Ishi Kawashima Harima Heavy Industries Co., Ltd. (72) Inventor Harunobu Sakabe Otemachi, Chiyoda-ku, Tokyo 2-2-1 Ishi Kawashima Harima Heavy Industries Co., Ltd.

Claims (5)

【特許請求の範囲】[Claims] 【請求項1】 炭素系可燃物質で形成される充填層
(2)を備え、前記充填層(2)の上面よりも低い位置
で前記充填層(2)の横断方向の外周部に、前記充填層
(2)に連通する環状の燃焼空間(4)を備え、前記燃
焼空間(4)に廃棄物を粉末状で吹き込んで、前記燃焼
空間(4)及び前記充填層(2)において前記廃棄物を
燃焼させるとともに溶融スラグ化する廃棄物溶融炉であ
って、前記燃焼空間(4)と前記充填層(2)の境界位
置に、前記燃焼空間(4)の上部側より下方に張り出し
た下垂壁(8)を備えた廃棄物溶融炉。
1. A filling layer (2) formed of a carbon-based combustible material, the filling layer (2) being provided at a position lower than an upper surface of the filling layer (2) in a transverse direction outer peripheral portion of the filling layer (2). An annular combustion space (4) communicating with the bed (2) is provided, and the waste material is blown into the combustion space (4) in a powder form, and the waste material is provided in the combustion space (4) and the packed bed (2). Is a waste melting furnace that burns fuel and transforms it into molten slag, at the boundary position between the combustion space (4) and the packed bed (2), a drooping wall protruding downward from the upper side of the combustion space (4). Waste melting furnace with (8).
【請求項2】 炭素系可燃物質で形成される充填層
(2)を備え、前記充填層(2)の上面よりも低い位置
で前記充填層(2)の横断方向の外周部に、前記充填層
(2)に連通する環状の燃焼空間(4)を備え、前記燃
焼空間(4)に廃棄物を粉末状で吹き込んで、前記燃焼
空間(4)及び前記充填層(2)において前記廃棄物を
燃焼させるとともに溶融スラグ化する廃棄物溶融炉であ
って、前記燃焼空間(4)より前記充填層(2)へ移流
する燃焼ガスの流れ方向が、斜め下向きに設定されてい
る廃棄物溶融炉。
2. A filling layer (2) formed of a carbon-based combustible material, the filling layer (2) being provided at a position lower than an upper surface of the filling layer (2) in an outer peripheral portion in a transverse direction of the filling layer (2). An annular combustion space (4) communicating with the bed (2) is provided, and the waste material is blown into the combustion space (4) in a powder form, and the waste material is provided in the combustion space (4) and the packed bed (2). A waste melting furnace that burns gas and melts into slag, and the flow direction of the combustion gas advancing from the combustion space (4) to the packed bed (2) is set obliquely downward. .
【請求項3】 周方向に分散した複数の導入部位(4
2)から気体搬送状態の前記廃棄物を前記燃焼空間
(4)に供給する供給手段が、前記燃焼空間(4)の周
部に備えられ、前記供給手段による前記廃棄物の供給方
向が、前記環状の燃焼空間(4)に旋回流(F)を形成
する向きに設定されている請求項1もしくは2記載の廃
棄物溶融炉。
3. A plurality of introduction sites (4) dispersed in the circumferential direction.
A supply means for supplying the waste in a gas-carrying state from 2) to the combustion space (4) is provided in a peripheral portion of the combustion space (4), and a supply direction of the waste by the supply means is the above-mentioned. The waste melting furnace according to claim 1 or 2, wherein the waste melting furnace is set so as to form a swirl flow (F) in the annular combustion space (4).
【請求項4】 前記供給手段が、前記廃棄物を前記導入
部位(42)に導く第一導入路(43a)を備えるとと
もに、前記第一導入路(43a)の周部に形成され且つ
酸素含有ガスを前記導入部位(42)の近傍に導く第二
導入路(43b)を備え、前記導入部位(42)におい
て、前記酸素含有ガスを前記廃棄物の周りに螺旋状の旋
回流として供給する旋回供給手段が備えられている請求
項3記載の廃棄物溶融炉。
4. The supply means comprises a first introducing passage (43a) for guiding the waste to the introducing portion (42), and is formed in a peripheral portion of the first introducing passage (43a) and contains oxygen. A swirl provided with a second introduction path (43b) for guiding the gas to the vicinity of the introduction part (42), and supplying the oxygen-containing gas as a spiral swirl flow around the waste at the introduction part (42). The waste melting furnace according to claim 3, further comprising a supply means.
【請求項5】 請求項3記載の廃棄物溶融炉に対する前
記廃棄物の供給方法であって、前記供給手段により、前
記複数の導入部位(42)において、前記燃焼空間
(4)の周方向で順次、廃棄物供給、廃棄物供給停止を
行い、前記燃焼空間(4)に形成される旋回流(F)の
旋回を促進もしくは抑制制御する廃棄物の供給方法。
5. The method for supplying the waste to the waste melting furnace according to claim 3, wherein the supply means is provided in the circumferential direction of the combustion space (4) at the plurality of introduction portions (42). A method of supplying waste, in which the supply of waste and the stop of supply of waste are sequentially performed to accelerate or suppress the swirling of the swirling flow (F) formed in the combustion space (4).
JP05060672A 1992-03-30 1993-03-19 Waste melting furnace and waste supply method Expired - Fee Related JP3081402B2 (en)

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JP4-71807 1992-03-30
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Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2005080874A1 (en) * 2004-02-24 2005-09-01 Nippon Steel Corporation Waste fusion treatment method utilizing powdery biomass

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2005080874A1 (en) * 2004-02-24 2005-09-01 Nippon Steel Corporation Waste fusion treatment method utilizing powdery biomass

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