JPS63315822A - Waste disposing apparatus - Google Patents

Waste disposing apparatus

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Publication number
JPS63315822A
JPS63315822A JP14952487A JP14952487A JPS63315822A JP S63315822 A JPS63315822 A JP S63315822A JP 14952487 A JP14952487 A JP 14952487A JP 14952487 A JP14952487 A JP 14952487A JP S63315822 A JPS63315822 A JP S63315822A
Authority
JP
Japan
Prior art keywords
melting furnace
fluidized bed
exhaust gas
incinerated ash
discharge port
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.)
Pending
Application number
JP14952487A
Other languages
Japanese (ja)
Inventor
Kotaro Taniguchi
谷口 興太郎
Takashige Ishida
石田 喬重
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.)
Kubota Corp
Original Assignee
Kubota Corp
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Kubota Corp filed Critical Kubota Corp
Priority to JP14952487A priority Critical patent/JPS63315822A/en
Publication of JPS63315822A publication Critical patent/JPS63315822A/en
Pending legal-status Critical Current

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  • Incineration Of Waste (AREA)
  • Fluidized-Bed Combustion And Resonant Combustion (AREA)

Abstract

PURPOSE:To enable collection and melting of most of incinerated ash content, by a method wherein the exhaust gas outlet of an incinerator is located in a level higher than that of the discharge port of incinerated ash content. CONSTITUTION:An opening 9 of the upper end part of an exhaust pipe 8 in which a discharge passage R through which incinerated ash content is forced to flow down from a fluidized bed 1 together with combustion exhaust gas for take out is mounted to a fluidized bed furnace 7 in a level lower than that of the upper end of the fluidized bed 1. A melting furnace 10 to melt incinerated ash content taken out through the discharge passage R is situated below, a discharge port 11 of the discharge passage R is situated in the melting furnace 10, and an exhaust gas outlet 12 of the melting furnace 10 is positioned in a level higher than that of the discharge port 11. When the incinerated ash content of a layer of coarseness C1 of the fluidized bed 1 is forced to flow down through the discharge passage R, a sufficient amount of particles having high apparent specific gravity and grain size can be collected by the melting furnace 10. Further, since a portion in the vicinity of the discharge port 11 is heated to 1000 deg.C by means of a secondary burner 15, when the incinerated ash content heated in a combustion chamber 16 to 800-900 deg.C is further dropped in the melting furnace 10 through the discharge port 11, it is heated to 1000 deg.C, and melting is promoted.

Description

【発明の詳細な説明】 〔産業上の利用分野〕 本発明は、廃棄物処理装置に関する。[Detailed description of the invention] [Industrial application field] The present invention relates to a waste treatment device.

〔従来の技術〕[Conventional technology]

従来の廃棄物処理装置では、流動層炉における流動層の
上端よりも高いレベルに、焼却灰分を燃焼排ガスと共に
上昇させて取出す排出路に対する接続用開口を配置し、
排出路からの焼却灰分を燃焼排ガス中から捕集する電気
集塵器を設けてあった。
In conventional waste treatment equipment, a connection opening for a discharge passage through which incinerated ash is raised and taken out together with combustion exhaust gas is arranged at a level higher than the upper end of the fluidized bed in a fluidized bed furnace.
An electrostatic precipitator was installed to collect incinerated ash from the exhaust gas from the exhaust gas.

〔発明が解決しようとする問題点〕[Problem that the invention seeks to solve]

しかし、燃焼排ガスと共に上昇させて取出される焼却灰
分は、見かけ比重が小さく粒子も小さいために、大部分
が電気集塵器でしか捕集することができず、電気集塵器
の容量を太き(しなければならないと共に、電気集塵器
で捕集した焼却灰分は、溶融炉に移して溶融するまでに
−冷えてしまい、熱損失が大きいという欠点があった。
However, since the incinerated ash that rises with the combustion exhaust gas and is extracted has a small apparent specific gravity and small particles, most of it can only be collected by an electrostatic precipitator, which requires an increase in the capacity of the electrostatic precipitator. In addition, the incinerated ash collected by the electrostatic precipitator cools down by the time it is transferred to the melting furnace and melted, resulting in a large heat loss.

本発明の目的は、大容量の電気集塵器を使用せずに焼却
灰分の大部分を捕集できるようにすると共に、熱損失を
小さくしながら焼却灰分を溶融できるようにする点にあ
る。
An object of the present invention is to be able to collect most of the incinerated ash without using a large-capacity electrostatic precipitator, and to melt the incinerated ash while reducing heat loss.

〔問題点を解決するための手段〕[Means for solving problems]

本発明の廃棄物処理装置の特徴構成は、流動層炉におけ
る流動層の上端よりも低いレベルに、焼却灰分を燃焼排
ガスと共に流下させて取出す排出路に対する接続用開口
を配置し、前記排出路からの焼却灰分を溶融する溶融炉
を設け1.前記排出路の排出口を、下方に向けて前記溶
融炉内に配置すると共に、前記溶融炉の排ガス出口を、
前記排出口よりも高い位置に配置してあることにあり、
その作用効果は、次の通りである。
A characteristic configuration of the waste treatment apparatus of the present invention is that a connection opening for a discharge passage through which incinerated ash is allowed to flow down and taken out together with combustion exhaust gas is arranged at a level lower than the upper end of the fluidized bed in a fluidized bed furnace, and from the discharge passage. A melting furnace is installed to melt the incinerated ash of 1. The discharge port of the discharge passage is arranged in the melting furnace with the discharge port facing downward, and the exhaust gas outlet of the melting furnace is
The reason is that it is located at a higher position than the outlet,
Its effects are as follows.

〔作 用〕[For production]

つまり、流動層炉における処理物は、流動層内で激しく
衝突を繰り返し、通常、燃焼及び灰化の促進に伴い、見
掛比重が小さくなると共に粒子も小さくなっていき、最
後には流動層の上◇:IHより上方に燃焼排ガスと共に
飛び出してしまい再び落下して来なくなる。そのために
、流動層の上端よりも低いレベルに配置した開口からは
、従来に比して見掛比重や粒子径の大きい焼却灰分が排
出路に流れ込む。そして排出路を流下する焼却灰分は、
見掛比重及び粒子径が大きいために、溶融炉内で排出口
から下方に落下して底部に溜りやすく、しかも、溶融炉
の排ガス出口を排出口よりも高い位置に配置してあるた
めに、排出口より出た燃焼排ガスが排ガス出口まで上昇
する際に、サイクロン作用によって排ガス中から焼却灰
分の大部分が分離されて溶融炉の底部に落下し、溶融す
る。
In other words, the processed material in a fluidized bed furnace repeatedly collides violently within the fluidized bed, and as combustion and ashing are promoted, the apparent specific gravity becomes smaller and the particles become smaller. Top ◇: It flies out with the combustion exhaust gas above the IH and does not come back down. Therefore, incinerated ash having a larger apparent specific gravity and larger particle size than in the past flows into the discharge channel from the openings arranged at a level lower than the upper end of the fluidized bed. The incinerated ash flowing down the discharge channel is
Because of their large apparent specific gravity and particle size, they tend to fall downward from the discharge port in the melting furnace and accumulate at the bottom.Moreover, because the exhaust gas outlet of the melting furnace is located at a higher position than the discharge port, When the combustion exhaust gas discharged from the exhaust port rises to the exhaust gas outlet, most of the incinerated ash is separated from the exhaust gas by cyclone action, falls to the bottom of the melting furnace, and is melted.

〔発明の効果〕〔Effect of the invention〕

従って、大容量の電気集塵器を使用して排ガス中より焼
却天分を捕集せずとも、大部分の焼却灰分が溶融炉で捕
集され、しかも冷えてしまうことなく迅速に溶融してし
まえるために、熱損失少なく廃棄物処理のだめの設備費
、及び処理費用を安(することができるようになった。
Therefore, without using a large-capacity electrostatic precipitator to collect incineration components from the exhaust gas, most of the incineration ash can be collected in the melting furnace and melted quickly without cooling. Because of this, it has become possible to reduce the cost of waste disposal facilities and processing costs due to less heat loss.

〔実施例〕〔Example〕

次に、本発明の実施例を、図面に基づいて説明する。 Next, embodiments of the present invention will be described based on the drawings.

第1図に示すように、内部下方側に砂等の゛流動媒体を
充填して流動層(1)を形成し、−次空気送風機(2)
からのエアーを流動層(1)に供給する複数の散気孔(
3)を備えた底部(4)を流動層(1)の下方に設け、
流動層(1)の上方に、ホッパー(6)に供給貯留され
る被焼却物をスクリューコンベア(5)等を介して供給
するべ(構成してあり、もって、流動媒体を高温かつ流
動化させ、水分20〜50%含有する下水処理によって
取出される汚泥あるいは都市塵埃等の被焼却物を浮遊燃
焼させて焼却処理していく流動層炉(7)を設け、焼却
灰分を燃焼排ガスと共に流動層(1)より流下させて取
出す排出路(R)が内部に形成される排出管(8)を、
上下方向に向けると共に、その上端部の開口(9)を流
動層(1)の上端よりも低いレベルで、平面視における
中央位置に配置する状態で流動層炉(7)に取付け、前
記排出路(R)からの焼却灰分を溶融する溶融炉(10
)を流動層炉(7)の下方に配置して設け、排出路(R
)の排出口(11)を、下方に向けて溶融炉(10)内
に配置すると共に、溶融炉(10)の排ガス出口(12
)を、排出口(11)よりも高い位置に配置して、溶融
炉(10)にサイクロン機能を備えさせて、廃!¥!I
J処理装置を構成してある。
As shown in Figure 1, a fluidized bed (1) is formed by filling the lower part of the interior with a fluidized medium such as sand, and a secondary air blower (2) is formed.
A plurality of diffuser holes (
3) is provided below the fluidized bed (1);
Above the fluidized bed (1), the material to be incinerated is supplied to the hopper (6) via a screw conveyor (5) etc. A fluidized bed furnace (7) is installed to float and incinerate incinerated materials such as sludge or urban dust extracted from sewage treatment containing 20 to 50% moisture, and incinerate the incinerated ash together with the combustion exhaust gas in the fluidized bed. (1) A discharge pipe (8) in which a discharge path (R) is formed to be taken out by flowing down from the
It is attached to the fluidized bed furnace (7) with the opening (9) at the upper end thereof facing in the vertical direction and located at the center position in a plan view at a level lower than the upper end of the fluidized bed (1), and the discharge passage A melting furnace (10
) is arranged below the fluidized bed furnace (7), and a discharge passage (R
) is arranged in the melting furnace (10) with the outlet (11) facing downward, and the exhaust gas outlet (12) of the melting furnace (10)
) is placed at a higher position than the discharge port (11), the melting furnace (10) is equipped with a cyclone function, and the waste! ¥! I
A J processing device is configured.

前記流動層炉(7)の下部には、スクリューコンヘア(
13)を設けて、被焼却物中に含有する金属屑等の不燃
物や難燃物を排出するように構成すると共に、排出物中
に含まれる一部の流動床川砂及び灰等は、分離装置(2
7)で分離後、炉(7)内に戻し、残部は溶融炉(10
)に供給する。図中(14)は−次バーナで、燃焼開始
初期等において使用し、(15)は二次バーナで、排出
口(11)から排出される燃焼排ガス中の未燃ガスを二
次燃焼させるために、溶融炉(10)に設けである。尚
、前記二次バーナ(15)によって溶融炉(10)内の
排出口(11)付近は1000℃に加熱されるために、
流動層炉(7)内の燃焼室(16)で800〜900℃
に加熱された焼却灰分が、更に排出口(11)から溶融
炉(10)内に落下すると1000°Cに加熱されて溶
融の促進化が行われる。
At the bottom of the fluidized bed furnace (7), there is a screw conhair (
13) is installed to discharge incombustibles and flame retardants such as metal scraps contained in the incinerated materials, and some fluidized bed river sand and ash contained in the discharged materials are separated. Device (2
After separation in step 7), it is returned to the furnace (7), and the remainder is transferred to the melting furnace (10).
). In the figure, (14) is a negative burner, which is used at the beginning of combustion, and (15) is a secondary burner, which is used to perform secondary combustion of unburned gas in the combustion exhaust gas discharged from the exhaust port (11). It is provided in the melting furnace (10). In addition, since the vicinity of the discharge port (11) in the melting furnace (10) is heated to 1000°C by the secondary burner (15),
800-900℃ in the combustion chamber (16) in the fluidized bed furnace (7)
When the incinerated ash heated to 100° C. further falls into the melting furnace (10) from the discharge port (11), it is heated to 1000° C. to accelerate melting.

尚、二次バーナ(15)で未燃ガスを燃焼させるために
、エアーを補給する二次空気供給装置(17)が、その
エアー噴出口(18)を排出管(8)内で、且つ、排出
口(11)と同芯状に配置してある。
In addition, in order to burn unburned gas in the secondary burner (15), a secondary air supply device (17) that replenishes air has its air jet port (18) within the exhaust pipe (8), and It is arranged concentrically with the discharge port (11).

前記溶融炉(10)には、貯留した焼却天分をその内部
から溶融するための一対のモリブデン電極(19) 、
 (19)を設け、底部に溶融スラグを取出すだめのオ
リフィスプレートゲート(20)を設けてあり、溶融炉
(10)の上下中間位置には、排ガス出口(12)から
出た排ガス中から電気集塵器(21)によって捕集した
有害な低融点の重金属等から成るEP灰を溶融炉(10
)に貯留した焼却灰分中に供給する供給装置(22)を
設けである。
The melting furnace (10) includes a pair of molybdenum electrodes (19) for melting the stored incineration material from within.
(19), and an orifice plate gate (20) for taking out the molten slag is provided at the bottom, and an electric collector is installed in the upper and lower intermediate positions of the melting furnace (10) from the exhaust gas exiting from the exhaust gas outlet (12). The EP ash consisting of harmful low-melting point heavy metals etc. collected by the duster (21) is transferred to the melting furnace (10).
) is provided with a feeding device (22) for feeding into the incineration ash stored in the incineration ash.

図中(23)は排ガスを排ガス出口(12)から強制的
に誘引するファンで、(24)は廃熱回収装置である。
In the figure, (23) is a fan that forcibly draws exhaust gas from the exhaust gas outlet (12), and (24) is a waste heat recovery device.

また、前記排ガス出口(12)は、溶融炉(10)に対
して第2図に示すよう平面視で接線方向に向けて取付け
てあり、サイクロン作用を効果的に生じさせるように構
成してある。
Further, the exhaust gas outlet (12) is attached to the melting furnace (10) so as to face tangentially in a plan view as shown in FIG. 2, and is configured to effectively produce a cyclone effect. .

つまり、流動層(1)から飛出す以前の見掛は比重及び
粒子径の大きい焼却灰分が、燃焼排ガスと共に排出炉(
R)を通って下方に流下して溶融炉(10)の底部にそ
の大部分が堆積し、更に排ガスと共に溶融炉(10)内
を上昇しようとする焼却灰分の残部は、排出口(11)
から排ガス出口(12)まで炉内周壁(IOA)の周方
向に沿って旋回しながら上昇し、サイクロン作用によっ
て排ガスより分離されて下方に落下する。そして、溶融
炉(10)の下部に貯留された焼却天分は、モリブデン
電極(19)とバーナ(15)の併用によって1500
〜1600℃に加熱されてその内部から溶融されるため
に、天分中に含有する低融点の重金属は、上部の未溶融
の焼却天分によってカバーされた状態で、外気に気化飛
散することなく、他の焼却天分と共に溶融スラグとなっ
て前記オリフィスプレートゲ−1−(20)の開度調整
操作によって適量づつ取出され、コンヘア(25)上を
空冷されながら固化する。
In other words, the incinerated ash, which apparently has a large specific gravity and particle size before flying out from the fluidized bed (1), is mixed with the combustion exhaust gas in the exhaust furnace (
The remaining part of the incinerated ash, which flows downward through R) and deposits most of it at the bottom of the melting furnace (10), and further rises in the melting furnace (10) together with the exhaust gas, is discharged through the discharge port (11).
The gas rises while rotating along the circumferential direction of the inner furnace wall (IOA) from to the exhaust gas outlet (12), is separated from the exhaust gas by the cyclone action, and falls downward. Then, the incineration material stored in the lower part of the melting furnace (10) is reduced to 1,500 by using the molybdenum electrode (19) and burner (15)
Because it is heated to ~1600℃ and melted from within, the heavy metals with a low melting point contained in the ingredients are covered by the unmelted incinerated ingredients above and are not vaporized and scattered into the outside air. The molten slag becomes molten slag together with other incineration materials, and is taken out in appropriate amounts by adjusting the opening of the orifice plate game 1-(20), and is solidified while being air-cooled on the container hair (25).

前記流動層炉(7)において、第3図に粒子径、見掛比
重別の流動化開始速度(A)と終端速度(B)の関係を
示し、この関係から、例えば被焼却物が1u径で3.0
の比重(ρ)の場合、炉内に正常な形の流動層(1)を
形成させるために、0.2m/sec、の開始速度(A
)以上で約10m/sec、の終端速度(B)以内の速
度に設定して運転しなければならず、そこで最適流動加
速度を5 m/sec、とすれば、見掛比重(ρ)=0
.3の物質では、粒子径が約2mm以下になると、流動
層(1)より外方に飛出し、電気集塵器(21)でなけ
れば捕集困難なフライアッシュになるものである。
In the fluidized bed furnace (7), Fig. 3 shows the relationship between the fluidization start speed (A) and the final speed (B) for each particle size and apparent specific gravity. So 3.0
For a specific gravity (ρ) of 0.2 m/sec, a starting velocity (A
), it must be operated at a speed within the terminal speed (B) of approximately 10 m/sec, and if the optimum flow acceleration is 5 m/sec, the apparent specific gravity (ρ) = 0.
.. In the case of the substance No. 3, when the particle size becomes about 2 mm or less, it flies out of the fluidized bed (1) and becomes fly ash, which is difficult to collect except with an electrostatic precipitator (21).

そこで、前記流動層(1)を第1図に示すように、粗(
C+)、 (CZ)と密(0)の層になるように流動化
させ、その粗(C1)の層の焼却灰分を排出路(R)よ
り流下させて取出せば、上記フライアッシュよりも見掛
比重(ρ)及び粒子径の大きな粒子が取出され、溶融炉
(10)によって十分捕集できることになる。
Therefore, as shown in FIG. 1, the fluidized bed (1) is
C+), (CZ) and dense (0) layers, and if the incinerated ash in the coarse (C1) layer is allowed to flow down through the discharge channel (R) and taken out, it will be more visible than the fly ash mentioned above. Particles with large specific gravity (ρ) and particle size are taken out and can be sufficiently collected by the melting furnace (10).

尚、第1図中の(26)は、分散板で上方から供給した
被焼却物が均等に分散するように形成してある。
Note that (26) in FIG. 1 is a dispersion plate formed so that the materials to be incinerated supplied from above are evenly dispersed.

〔別宴絶倒〕[Awesome party]

前記開口(9)は、流動層炉(7)の平面視で中央に限
らず、内周壁よりもしくは内周壁に配置してあっても良
い。
The opening (9) is not limited to the center in a plan view of the fluidized bed furnace (7), but may be located closer to or on the inner peripheral wall.

尚、特許請求の範囲の項に図面との対照を便利にする為
に符号を記すが、該記入により本発明は添付図面の構造
に限定されるものではない。
Incidentally, although reference numerals are written in the claims section for convenient comparison with the drawings, the present invention is not limited to the structure shown in the accompanying drawings.

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

図面は本発明に係る廃棄物処理装置の実施例を示し、第
1図は全体の縦断面図、第2図は第1図における■−■
線断面図、第3図はグラフである。 (1)・・・・・・流動層、(7)・・・・・・流動層
炉、(9)・・・・・・開口、(10)・・・・・・溶
融炉、(11)・・・・・・排出口、(12)・・・・
・・排ガス出口、(R)・・・・・・排出路。
The drawings show an embodiment of the waste treatment apparatus according to the present invention, and FIG. 1 is a longitudinal cross-sectional view of the whole, and FIG. 2 is a cross-sectional view of ■-■ in FIG.
The line cross-sectional view and FIG. 3 are graphs. (1)...Fluidized bed, (7)...Fluidized bed furnace, (9)...Opening, (10)...Melting furnace, (11 )...Exhaust port, (12)...
...Exhaust gas outlet, (R)...Exhaust path.

Claims (1)

【特許請求の範囲】[Claims] 流動層炉(7)における流動層(1)の上端よりも低い
レベルに、焼却灰分を燃焼排ガスと共に流下させて取出
す排出路(R)に対する接続用開口(9)を配置し、前
記排出路(R)からの焼却灰分を溶融する溶融炉(10
)を設け、前記排出路(R)の排出口(11)を、下方
に向けて前記溶融炉(10)内に配置すると共に、前記
溶融炉(10)の排ガス出口(12)を、前記排出口(
11)よりも高い位置に配置してある廃棄物処理装置。
A connecting opening (9) for a discharge passage (R) through which incinerated ash is allowed to flow down and taken out together with combustion exhaust gas is disposed at a level lower than the upper end of the fluidized bed (1) in the fluidized bed furnace (7). A melting furnace (10
), and the discharge port (11) of the discharge passage (R) is arranged in the melting furnace (10) facing downward, and the exhaust gas outlet (12) of the melting furnace (10) is connected to the exhaust gas outlet (12). Exit(
11) Waste treatment equipment located at a higher position than the
JP14952487A 1987-06-15 1987-06-15 Waste disposing apparatus Pending JPS63315822A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP14952487A JPS63315822A (en) 1987-06-15 1987-06-15 Waste disposing apparatus

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP14952487A JPS63315822A (en) 1987-06-15 1987-06-15 Waste disposing apparatus

Publications (1)

Publication Number Publication Date
JPS63315822A true JPS63315822A (en) 1988-12-23

Family

ID=15477019

Family Applications (1)

Application Number Title Priority Date Filing Date
JP14952487A Pending JPS63315822A (en) 1987-06-15 1987-06-15 Waste disposing apparatus

Country Status (1)

Country Link
JP (1) JPS63315822A (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
EP1111304A3 (en) * 1994-03-10 2001-09-05 Ebara Corporation Method of and apparatus for fluidized-bed gasification and melt combustion

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
EP1111304A3 (en) * 1994-03-10 2001-09-05 Ebara Corporation Method of and apparatus for fluidized-bed gasification and melt combustion
EP1286113A3 (en) * 1994-03-10 2003-03-05 Ebara Corporation Method and apparatus for fluidized-bed gasification and melt combustion

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