JPH04687B2 - - Google Patents
Info
- Publication number
- JPH04687B2 JPH04687B2 JP62175493A JP17549387A JPH04687B2 JP H04687 B2 JPH04687 B2 JP H04687B2 JP 62175493 A JP62175493 A JP 62175493A JP 17549387 A JP17549387 A JP 17549387A JP H04687 B2 JPH04687 B2 JP H04687B2
- Authority
- JP
- Japan
- Prior art keywords
- exhaust gas
- lime powder
- moving layer
- dust
- gas
- 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.)
- Expired - Lifetime
Links
- 239000007789 gas Substances 0.000 claims description 85
- 239000000843 powder Substances 0.000 claims description 39
- 235000008733 Citrus aurantifolia Nutrition 0.000 claims description 36
- 235000011941 Tilia x europaea Nutrition 0.000 claims description 36
- 239000004571 lime Substances 0.000 claims description 36
- 239000000428 dust Substances 0.000 claims description 22
- 239000000969 carrier Substances 0.000 claims description 7
- 238000002485 combustion reaction Methods 0.000 claims description 4
- 239000004576 sand Substances 0.000 claims description 4
- 230000005484 gravity Effects 0.000 claims description 3
- 231100001261 hazardous Toxicity 0.000 claims description 3
- 239000012717 electrostatic precipitator Substances 0.000 description 19
- ODINCKMPIJJUCX-UHFFFAOYSA-N Calcium oxide Chemical compound [Ca]=O ODINCKMPIJJUCX-UHFFFAOYSA-N 0.000 description 10
- VEXZGXHMUGYJMC-UHFFFAOYSA-N Hydrochloric acid Chemical compound Cl VEXZGXHMUGYJMC-UHFFFAOYSA-N 0.000 description 7
- VYPSYNLAJGMNEJ-UHFFFAOYSA-N Silicium dioxide Chemical compound O=[Si]=O VYPSYNLAJGMNEJ-UHFFFAOYSA-N 0.000 description 7
- 229910000041 hydrogen chloride Inorganic materials 0.000 description 7
- IXCSERBJSXMMFS-UHFFFAOYSA-N hydrogen chloride Substances Cl.Cl IXCSERBJSXMMFS-UHFFFAOYSA-N 0.000 description 7
- AXCZMVOFGPJBDE-UHFFFAOYSA-L calcium dihydroxide Chemical compound [OH-].[OH-].[Ca+2] AXCZMVOFGPJBDE-UHFFFAOYSA-L 0.000 description 5
- 239000000920 calcium hydroxide Substances 0.000 description 5
- 235000011116 calcium hydroxide Nutrition 0.000 description 5
- 229910001861 calcium hydroxide Inorganic materials 0.000 description 5
- 239000000292 calcium oxide Substances 0.000 description 5
- 235000012255 calcium oxide Nutrition 0.000 description 5
- 229910052815 sulfur oxide Inorganic materials 0.000 description 5
- 238000001816 cooling Methods 0.000 description 3
- 235000019738 Limestone Nutrition 0.000 description 2
- 238000007664 blowing Methods 0.000 description 2
- OSGAYBCDTDRGGQ-UHFFFAOYSA-L calcium sulfate Chemical compound [Ca+2].[O-]S([O-])(=O)=O OSGAYBCDTDRGGQ-UHFFFAOYSA-L 0.000 description 2
- 238000006243 chemical reaction Methods 0.000 description 2
- 238000007599 discharging Methods 0.000 description 2
- 230000000694 effects Effects 0.000 description 2
- 239000006028 limestone Substances 0.000 description 2
- 239000000463 material Substances 0.000 description 2
- 229920003023 plastic Polymers 0.000 description 2
- 239000004033 plastic Substances 0.000 description 2
- 239000000377 silicon dioxide Substances 0.000 description 2
- XTQHKBHJIVJGKJ-UHFFFAOYSA-N sulfur monoxide Chemical class S=O XTQHKBHJIVJGKJ-UHFFFAOYSA-N 0.000 description 2
- 238000005979 thermal decomposition reaction Methods 0.000 description 2
- UXVMQQNJUSDDNG-UHFFFAOYSA-L Calcium chloride Chemical compound [Cl-].[Cl-].[Ca+2] UXVMQQNJUSDDNG-UHFFFAOYSA-L 0.000 description 1
- 239000011575 calcium Substances 0.000 description 1
- 239000001110 calcium chloride Substances 0.000 description 1
- 229910001628 calcium chloride Inorganic materials 0.000 description 1
- 239000004568 cement Substances 0.000 description 1
- 238000010586 diagram Methods 0.000 description 1
- 238000005516 engineering process Methods 0.000 description 1
- 238000009434 installation Methods 0.000 description 1
- 238000000034 method Methods 0.000 description 1
- 239000002893 slag Substances 0.000 description 1
Landscapes
- Treating Waste Gases (AREA)
- Gas Separation By Absorption (AREA)
Description
【発明の詳細な説明】
〔産業上の利用分野〕
本発明は、焼却炉などから排気される塩化水素
やイオウ酸化物などの有害ガスを含む排ガスに石
灰粉を吹き込んで有害ガスを除去するための有害
ガス処理装置に関するものである。[Detailed Description of the Invention] [Industrial Application Field] The present invention is a method for removing harmful gases by blowing lime powder into exhaust gas containing harmful gases such as hydrogen chloride and sulfur oxides exhausted from an incinerator or the like. The present invention relates to a hazardous gas treatment device.
焼却炉から排気される燃焼排ガスには、焼却物
中に含まれる塩ビ系プラスチツクの熱分解により
600〜1000ppmの塩化水素やイオウ酸化物(SOx)
などの有害ガスが含まれている。
The combustion exhaust gas exhausted from the incinerator is caused by the thermal decomposition of PVC plastics contained in the incinerated materials.
600-1000ppm hydrogen chloride and sulfur oxides (SOx)
Contains harmful gases such as
従来、この有害ガスを乾式で除去するには、排
ガス中に消石灰や生石灰などの石灰粉を噴射して
除去することがなされているが、排ガスと石灰粉
の接触が十分でないため除去率が低い問題があ
る。 Traditionally, this harmful gas has been removed dryly by injecting lime powder such as slaked lime or quicklime into the exhaust gas, but the removal rate is low because there is insufficient contact between the exhaust gas and lime powder. There's a problem.
このため、排ガスを生石灰などの充填移動層を
通して塩化水素を除去することがなされている。
すなわち、排ガス流に対して打ち抜き板やスクリ
ーンなど或はルーバーなどを対向させて配置し、
その間に生石灰を充填すると共にそれを降下循環
させて充填移動層を形成し、その移動層内に排ガ
スを通すことで有害ガスを除去するようにしてい
る。 For this reason, hydrogen chloride is removed from the exhaust gas by passing it through a moving bed filled with quicklime or the like.
In other words, a punched plate, screen, or louver is placed facing the exhaust gas flow.
In the meantime, quicklime is filled and circulated downward to form a packed moving bed, and harmful gases are removed by passing exhaust gas through the moving bed.
しかしながら、この充填移動層式の排ガス処理
装置は、高含じんガスあるいはガス速度が速い場
合は、圧力損失が高くなり過ぎるため、電気集じ
ん器の後流に設置すると共に充填移動層の断面積
を大きくとり、ガス速度を0.2m/sec位に下げて
いる。そのため設置面積が大きく、価格も高くな
る問題がある。
However, this packed moving bed type exhaust gas treatment equipment is installed downstream of the electrostatic precipitator, and the cross-sectional area of the packed moving bed is The gas velocity is lowered to around 0.2m/sec. Therefore, there are problems in that the installation area is large and the price is high.
排ガス中に消石灰粉等を吹き込み後流に担体を
充填した移動層を設け、有害ガス除去率を高めよ
うとする場合、充填移動層を電気集じん器の後流
に設置すれば、電気集じん器前に吹き込んだ消石
灰粉等が電気集じん器に捕集され移動層内での反
応が悪くなる。また、逆に電気集じん器の後流に
消石灰粉を吹き込めば、移動層の後流に再度電気
集じん器を設ける必要がある。 When attempting to increase the removal rate of harmful gases by blowing slaked lime powder etc. into the exhaust gas and installing a moving bed filled with a carrier downstream, if the filled moving bed is installed downstream of the electrostatic precipitator, the electrostatic precipitator will Slaked lime powder, etc. blown into the front of the vessel is collected by the electrostatic precipitator, which worsens the reaction within the moving bed. On the other hand, if slaked lime powder is blown into the wake of the electrostatic precipitator, it is necessary to install the electrostatic precipitator again in the wake of the moving layer.
そこで、充填移動層を電気集じん器の前に設置
し、なお且つ装置をコンパクトにするために充填
移動層を電気集じん器の前面に同一断面積で設置
しようとすると、充填移動層入口ガス条件は高含
じんガスであり、なお且つ電気集じん器内のガス
速度(約0.6m/sec)と同等の通過速度で運転す
ることとなり、従来の充填移動層の速度(約
0.2m/sec)の3倍程度となり、圧力損失を下げ
る対策が必要である。 Therefore, if you install the packed moving bed in front of the electrostatic precipitator, and if you try to install the packed moving bed in front of the electrostatic precipitator with the same cross-sectional area in order to make the device more compact, the filling moving bed inlet gas The conditions were high dust content gas, and the operation was to be carried out at a passage speed equivalent to the gas velocity in the electrostatic precipitator (approximately 0.6 m/sec), which was lower than that of a conventional packed moving bed (approximately 0.6 m/sec).
0.2m/sec), and measures to reduce pressure loss are required.
本発明は、上記事情を考慮してなされたもの
で、高含じんガスで電気集じん器内のガス速度と
同じ速度の排ガスを充填移動層に通しコンパクト
であり、且つ高除去率を有する有害ガス除去装置
を提供することを目的とする。 The present invention has been made in consideration of the above circumstances, and is a compact, highly dust-removal device that passes exhaust gas with high dust content and the same velocity as the gas velocity in the electrostatic precipitator through a packed moving bed. The purpose is to provide a gas removal device.
本発明は、上記の目的を達成するために、焼却
炉等から排気される有害ガスを含む燃焼排ガスに
石灰粉を吹き込み、この吹き込まれて有害ガスと
反応した石灰粉および未反応の石灰粉をダストと
共に排ガスから除去する有害ガス処理装置におい
て、排ガスを導入するケーシング内に、排ガスの
流れに対して横断するよう重力方向に移動し、上
記石灰粉を捕捉するための砂などの担体からなる
移動層を形成し、該移動層の前後両側に上下所定
間隔を隔ててルーバーを設け、その前後のルーバ
ーを互いに上下にずらせると共に各ルーバーを移
動層の中心下方に向けて傾斜させ、かつ移動層の
担体の前後のルーバーで交互に保持して互いに近
接させて設け、さらにその移動層が形成されたケ
ーシングの後方に移動層から飛散したダスト等を
除去するための集じん器を設けたもので、先ず排
ガス中に石灰粉を吹き込み、塩化水素などの有害
ガスと反応した石灰粉および未反応の石灰粉をダ
ストと共に移動層で捕捉し、しかもその移動層で
排ガス中の未反応有害ガスを捕捉した未反応の石
灰粉と接触させることで有害ガスの除去率を高
め、かつ前後のルーバーを近接させると共に上下
にずらして設けることで、担体を前後のルーバー
に保持させながら降下移動させて排ガスとの接触
を良好にし、かつガス速度が高くてもダストなど
による目詰まりが生ぜず、さらにこの移動層の後
流のケーシングに電気集じん器を一体に設けるこ
とでガス速度をそのまま維持しながら移動層から
飛散したダスト等を除去できるようにしたもので
ある。
In order to achieve the above object, the present invention blows lime powder into combustion exhaust gas containing harmful gases exhausted from an incinerator, etc., and removes lime powder that has reacted with the harmful gases and unreacted lime powder. In a hazardous gas treatment device that removes dust from exhaust gas, a carrier such as sand moves in the direction of gravity so as to be transverse to the flow of exhaust gas and captures the lime powder in the casing into which the exhaust gas is introduced. A layer is formed, louvers are provided at a predetermined interval above and below on both sides of the moving layer, the front and rear louvers are shifted vertically from each other, and each louver is tilted downward from the center of the moving layer; The carriers are alternately held by front and rear louvers and placed close to each other, and a dust collector is installed behind the casing in which the moving layer is formed to remove dust etc. scattered from the moving layer. First, lime powder is blown into the exhaust gas, and the lime powder that has reacted with harmful gases such as hydrogen chloride and unreacted lime powder are captured together with the dust in a moving layer, and the unreacted harmful gases in the exhaust gas are captured in the moving layer. By bringing the carrier into contact with unreacted lime powder, the removal rate of harmful gases is increased, and by placing the front and rear louvers close to each other and shifting them up and down, the carrier is held by the front and rear louvers and moves downward, removing exhaust gas. This ensures good contact between the gases and prevents clogging due to dust even at high gas velocities.Furthermore, an electrostatic precipitator is integrated into the casing downstream of this moving layer, allowing the gas to move while maintaining the same velocity. This makes it possible to remove dust etc. scattered from the layer.
以下、本発明に係る有害ガス処理装置の好適一
実施例を添付図面に基づいて説明する。
DESCRIPTION OF THE PREFERRED EMBODIMENTS A preferred embodiment of a harmful gas treatment apparatus according to the present invention will be described below with reference to the accompanying drawings.
第1図において、1は流動床などの焼却炉で、
その排ガス出口にガス冷却装置2が接続され、そ
の後流にダクト3を介して有害ガス処理装置4が
接続され、その後流に誘引送風機5を介して煙突
6が接続されてゴミ焼却プラントが構成される。 In Figure 1, 1 is an incinerator such as a fluidized bed;
A gas cooling device 2 is connected to the exhaust gas outlet, a harmful gas treatment device 4 is connected to its downstream side through a duct 3, and a chimney 6 is connected to its downstream side through an induced blower 5, thereby forming a garbage incineration plant. Ru.
ガス冷却装置2から有害ガス処理装置4に至る
ダクト3には、そのダクト3内を通る排ガス中に
消石灰(Ca(OH)2)、生石灰(CaO)などの石灰
粉を吹き込むための石灰粉供給装置7が接続され
る。 A duct 3 leading from the gas cooling device 2 to the harmful gas treatment device 4 is supplied with lime powder for injecting lime powder such as slaked lime (Ca(OH) 2 ) or quicklime (CaO) into the exhaust gas passing through the duct 3. Device 7 is connected.
この石灰粉供給装置7は、石灰粉を排出するホ
ツパ8と、搬送空気を供給する送風機9と、ダク
ト3に接続する搬送ライン10とからなつてい
る。 The lime powder supply device 7 includes a hopper 8 for discharging lime powder, a blower 9 for supplying conveying air, and a conveying line 10 connected to the duct 3.
有害ガス処理装置4は、第2図に示すように石
灰粉が吹き込まれた排ガスを導入するケーシング
11からなり、そのケーシング11内に排ガスの
流れに対して横断するよう重力方向に移動する粒
状担体12からなる移動層13が形成され、その
移動層13の後流側ケーシング11に電気集じん
器14が設けられて構成される。 As shown in FIG. 2, the harmful gas treatment device 4 consists of a casing 11 into which the exhaust gas into which lime powder is blown is introduced, and inside the casing 11 there is a granular carrier that moves in the direction of gravity so as to be transverse to the flow of the exhaust gas. 12 is formed, and an electrostatic precipitator 14 is provided in the casing 11 on the downstream side of the moving layer 13.
移動層13は、第2図、第3図に示すようにそ
の前面側に前面ルーバー15が設けられ、後面側
に後面ルーバー16が設けられ、その間を珪砂、
石灰石、スラツグ、セメントクリンカなどの粒状
担体12が充填されて形成される。 As shown in FIGS. 2 and 3, the moving layer 13 is provided with a front louver 15 on its front side, a rear louver 16 on its rear side, and silica sand, silica sand, etc.
It is formed by being filled with a granular carrier 12 such as limestone, slag, cement clinker, etc.
前後のルーバー15,16は、ケーシング11
の上下方向に沿つて所定間隔を隔てて設けられる
と共に夫々前面ルーバー15と後面ルーバー16
との上下位置が互いにずれるよう設けられる。ま
た各ルーバー15,16は、夫々移動層13の中
心下方に向うよう傾斜され、かつ前後のルーバー
15,16が近接するよう設けられる。 The front and rear louvers 15 and 16 are connected to the casing 11
are provided at predetermined intervals along the vertical direction, and a front louver 15 and a rear louver 16, respectively.
and are provided so that their vertical positions are shifted from each other. Further, each of the louvers 15 and 16 is inclined downward from the center of the moving layer 13, and is provided so that the front and rear louvers 15 and 16 are close to each other.
ケーシング11の上部には、前後のルーバー1
5,16間に粒状担体12を供給するためのホツ
パー17が設けられ、また下部にはルーバー1
5,16間を降下した粒状担体12をケーシング
11の下部のホツパー18へ排出するためのロー
タ19が設けられる。 At the top of the casing 11 are front and rear louvers 1.
A hopper 17 for supplying the granular carrier 12 is provided between 5 and 16, and a louver 1 is provided at the bottom.
A rotor 19 is provided for discharging the granular carrier 12 that has descended between 5 and 16 to a hopper 18 at the bottom of the casing 11.
第1図に示すように下部ホツパー18に溜つた
粒状担体12等は分級器20に排出され、そこで
石灰粉やダストと粒状担体12とが分級され、粒
状担体12が垂直コンベア21を介して上部ホツ
パー17へ循環されるようになつている。 As shown in FIG. 1, the granular carriers 12 and the like accumulated in the lower hopper 18 are discharged to a classifier 20, where lime powder and dust are separated from the granular carriers 12, and the granular carriers 12 are transported to the upper part via a vertical conveyor 21. It is designed to be circulated to the hopper 17.
電気集じん器14は、第2図に示すように排ガ
ス流に対して複数枚平行に配設した集じん板22
と、その集じん板22間に沿つて多数配設した線
状の放電電極23からなつている。 The electrostatic precipitator 14 includes a plurality of dust collecting plates 22 arranged parallel to the exhaust gas flow as shown in FIG.
and a large number of linear discharge electrodes 23 arranged along between the dust collecting plates 22.
以上において、焼却炉1からは、焼却物中に含
まれる塩ビ系プラスチツクの熱分解により塩化水
素をなどの有害ガス含んだ燃焼排ガスが排気さ
れ、ガス冷却装置2でその熱量が回収されたの
ち、ダクト3に流れる。 In the above, combustion exhaust gas containing harmful gases such as hydrogen chloride is exhausted from the incinerator 1 due to the thermal decomposition of the PVC plastics contained in the incinerated material, and after its heat is recovered by the gas cooling device 2, Flows into duct 3.
ダクト3には、石灰粉供給装置7から石灰粉が
吹き込まれ、この石灰粉が排ガス中の塩化水素と
反応して塩化カルシウムとなり塩化水素を除去す
る。また、SOxの場合には石灰粉が硫酸カルシウ
ムとなりSOxを除去する。 Lime powder is blown into the duct 3 from a lime powder supply device 7, and this lime powder reacts with hydrogen chloride in the exhaust gas to become calcium chloride and remove the hydrogen chloride. In the case of SOx, lime powder turns into calcium sulfate and removes SOx.
この石灰粉が吹き込まれた排ガスは、ケーシン
グ11内に導入され、そこで前面ルーバー15を
通つて移動層13内を通り後面ルーバー16から
排気される間に排ガス中の石灰粉やダクトが捕捉
されることとなる。この場合、排ガス中の未反応
有害ガスは、この移動層13を通過する間に移動
層13内に捕捉された石灰粉或は粒状担体12に
石灰石を用いれば、その石灰粉や担体12と接触
し反応するため有害ガスの除去率を高くできる。 The exhaust gas into which the lime powder has been blown is introduced into the casing 11, where it passes through the front louver 15, the inside of the moving layer 13, and is exhausted from the rear louver 16, where lime powder and ducts in the exhaust gas are captured. That will happen. In this case, unreacted harmful gases in the exhaust gas will come into contact with the lime powder or the granular carrier 12 if limestone is used as the lime powder or granular carrier 12 that is trapped in the moving layer 13 while passing through the moving layer 13. Because of this reaction, the removal rate of harmful gases can be increased.
移動層13を降下する粒状担体は、第3図に示
すように前後のルーバー15,16が近接され、
かつ互いに上下にずらして配置されるため、前面
ルーバー15と後面ルーバー16とに交互に衝突
しながら図示の矢印のように降下して移動するた
め、移動層13が圧密にならずにダストや有害ガ
スと反応した石灰粉を捕捉でき、しかもその移動
層13を通過する排ガスの圧力損失を少なくでき
る。 As shown in FIG. 3, the granular carriers descending on the moving layer 13 are moved by the front and rear louvers 15 and 16 being brought close to each other, as shown in FIG.
In addition, since they are arranged vertically shifted from each other, they alternately collide with the front louver 15 and the rear louver 16 while descending and moving as shown by the arrows in the figure. Therefore, the moving layer 13 is not consolidated and dust and harmful The lime powder that has reacted with the gas can be captured, and the pressure loss of the exhaust gas passing through the moving layer 13 can be reduced.
前後のルーバー15,16は第4図に示すよう
に、ルーバー15,16の傾斜αを60度前後、上
下のルーバー15,16の垣隔Lを100mm程度、
前後のルーバー15,16の先端間の距離dを−
5mm〜25mm程度の範囲に保つことにより石灰粉や
ダストを良好に捕捉できると共に圧力損失の少な
い移動層13が形成でき、また適宜移動層13の
下方のロータ19の回転速度を調整することでそ
の移動層13内の担体12の降下速度を調整でき
る。 As shown in Fig. 4, the front and rear louvers 15, 16 have an inclination α of about 60 degrees, and a distance L between the upper and lower louvers 15, 16 of about 100 mm.
The distance d between the tips of the front and rear louvers 15 and 16 is −
By keeping the distance within the range of about 5 mm to 25 mm, lime powder and dust can be captured well and a moving layer 13 with low pressure loss can be formed. The descending speed of the carrier 12 within the moving layer 13 can be adjusted.
次に移動層13を通過した排ガス中には一部後
面ルーバー16間から飛散したダストや石灰粉が
含まれるが、そのケーシング11の後流に一体に
設置した電気集じん器14により除じんされる。 Next, the exhaust gas that has passed through the moving bed 13 contains some dust and lime powder scattered from between the rear louvers 16, but the dust and lime powder are removed by the electrostatic precipitator 14 installed integrally in the wake of the casing 11. Ru.
この電気集じん器14を通る排ガス流速は
0.6m/sec前後であるため、移動層13を通る排
ガス流速も、その流速となるようにする。 The exhaust gas flow rate passing through this electrostatic precipitator 14 is
Since it is approximately 0.6 m/sec, the flow velocity of the exhaust gas passing through the moving bed 13 is also set to be at this flow velocity.
尚電気集じん器14で除じんされかつ有害ガス
が除去された排ガスはクリーンなガスとして誘引
送風機5を介して煙突6から排出される。 The exhaust gas from which dust and harmful gases have been removed by the electrostatic precipitator 14 is discharged from the chimney 6 via the induced blower 5 as clean gas.
以上詳述してきたことから明らかなように本発
明によれば次のごとき優れた効果を発揮する。
As is clear from what has been described in detail above, the present invention exhibits the following excellent effects.
(1) 有害ガスを含む排ガス中に石灰粉を吹き込
み、その排ガスをルーバーで形成した担体の移
動層を通して排ガス中の石灰粉がダストを捕捉
することで有害ガスの除去率を高くできる。(1) Lime powder is blown into exhaust gas containing harmful gases, and the lime powder in the exhaust gas captures dust through a moving layer of carrier formed by louvers, increasing the removal rate of harmful gases.
(2) 前後のルーバーを近接し、かつ前後のルーバ
ーの位置を上下にずらすことで、移動層の担体
を前後のルーバーで交互に保持しながら降下で
きるので移動層が圧密化されず、高含じんガス
で電気集じん器のガス速度と同じ速度でも排ガ
スの圧力損失を少なくできる。(2) By placing the front and rear louvers close to each other and shifting the positions of the front and rear louvers up and down, the carriers of the moving bed can be lowered while being held alternately by the front and rear louvers, so the moving bed is not consolidated and high content can be achieved. Even if the dust gas is used at the same gas speed as the electrostatic precipitator, the pressure loss of the exhaust gas can be reduced.
(3) 移動層の後流側のケーシングに電気集じん器
を一体に設置し、そのガス速度を同じにするこ
とで装置をコンパクトにし移動層から飛散した
ダスト等を除じんできる。(3) By installing an electrostatic precipitator integrally in the casing on the downstream side of the moving bed and making the gas velocity the same, the device can be made compact and dust etc. scattered from the moving bed can be removed.
第1図は本発明の一実施例を示す全体図、第2
図は第1図の有害ガス処理装置の要部断面図、第
3図は第2図の移動層の詳細を示す断面図、第4
図は第3図のルーバーの詳細を示す図である。
図中、1は焼却炉、3はダクト、4は有害ガス
除去装置、7は石灰粉供給装置、11はケーシン
グ、12は担体、13は移動層、14は電気集じ
ん器、15は前面ルーバー、16は後面ルーバー
である。
FIG. 1 is an overall view showing one embodiment of the present invention, and FIG.
The figure is a cross-sectional view of the main part of the harmful gas treatment equipment in Figure 1, Figure 3 is a cross-sectional view showing details of the moving layer in Figure 2, and Figure 4 is a cross-sectional view showing the details of the moving layer in Figure 2.
The figure is a diagram showing details of the louver in FIG. 3. In the figure, 1 is an incinerator, 3 is a duct, 4 is a harmful gas removal device, 7 is a lime powder supply device, 11 is a casing, 12 is a carrier, 13 is a moving bed, 14 is an electrostatic precipitator, and 15 is a front louver. , 16 is a rear louver.
Claims (1)
排ガスに石灰粉を吹き込み、この吹き込まれて有
害ガスと反応した石灰粉および未反応の石灰粉と
をダストと共に排ガスから除去する有害ガス処理
装置において、排ガスを導入するケーシング内
に、排ガスの流れに対して横断するよう重力方向
に移動し、上記石灰粉を捕捉するための砂などの
担体からなる移動層を形成し、該移動層の前後両
側に上下所定間隔を隔ててルーバーを設け、その
前後のルーバーを互いに上下にずらせると共に各
ルーバーを移動層の中心下方に向けて傾斜させ、
かつ移動層の担体を前後のルーバーで交互に保持
して互いに近接させて設け、さらにその移動層が
形成されたケーシングの後方に移動層から飛散し
たダスト等を除去するための集じん器を一体に設
けたことを特徴とする有害ガス処理装置。1. In a harmful gas treatment device that blows lime powder into combustion exhaust gas containing harmful gases exhausted from an incinerator, etc., and removes lime powder that reacts with the harmful gas and unreacted lime powder from the exhaust gas along with dust. , a moving layer made of a carrier such as sand is formed in the casing into which exhaust gas is introduced, which moves in the direction of gravity so as to be transverse to the flow of the exhaust gas and captures the lime powder; louvers are provided at a predetermined interval above and below, the front and rear louvers are shifted vertically from each other, and each louver is tilted downward from the center of the moving layer;
In addition, the carriers of the moving layer are alternately held by front and rear louvers and placed close to each other, and a dust collector is integrated behind the casing in which the moving layer is formed to remove dust etc. scattered from the moving layer. A hazardous gas treatment device characterized by being installed in.
Applications Claiming Priority (2)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP61-146510 | 1986-09-26 | ||
| JP14651086 | 1986-09-26 |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPS63185433A JPS63185433A (en) | 1988-08-01 |
| JPH04687B2 true JPH04687B2 (en) | 1992-01-08 |
Family
ID=15409264
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP62175493A Granted JPS63185433A (en) | 1986-09-26 | 1987-07-14 | Harmful gas treatment equipment |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPS63185433A (en) |
Families Citing this family (3)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| US5624644A (en) * | 1994-11-02 | 1997-04-29 | Ets International, Inc. | Apparatus for acid gas emission control |
| JP2002282630A (en) * | 2001-03-29 | 2002-10-02 | Sumitomo Heavy Ind Ltd | Device and method for treating exhaust gas with improved dust removing performance |
| CN108430604A (en) * | 2016-04-11 | 2018-08-21 | 日挥株式会社 | Exhaust gas treatment system |
-
1987
- 1987-07-14 JP JP62175493A patent/JPS63185433A/en active Granted
Also Published As
| Publication number | Publication date |
|---|---|
| JPS63185433A (en) | 1988-08-01 |
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