JPH0857249A - Absorbing column - Google Patents

Absorbing column

Info

Publication number
JPH0857249A
JPH0857249A JP6200717A JP20071794A JPH0857249A JP H0857249 A JPH0857249 A JP H0857249A JP 6200717 A JP6200717 A JP 6200717A JP 20071794 A JP20071794 A JP 20071794A JP H0857249 A JPH0857249 A JP H0857249A
Authority
JP
Japan
Prior art keywords
absorbing
liquid
gas
air
soln
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
JP6200717A
Other languages
Japanese (ja)
Inventor
Fumihiko Yamaguchi
文彦 山口
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
Original Assignee
IHI 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 IHI Corp filed Critical IHI Corp
Priority to JP6200717A priority Critical patent/JPH0857249A/en
Publication of JPH0857249A publication Critical patent/JPH0857249A/en
Pending legal-status Critical Current

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  • Treating Waste Gases (AREA)
  • Gas Separation By Absorption (AREA)

Abstract

PURPOSE: To enhance gas-liquid contact and to efficiently oxidize sulfite, in an absorbing column, wherein air is blown into a liquid storage tank storing an absorbing soln. having absorbed and removed sulfur oxide from gas to be treated to oxidize sulfite, by providing a packed bed of a packing material in the absorbing soln. CONSTITUTION: A part of the absorbing soln. 4 in a liquid storage tank 5 is transferred to spray nozzles 7 by a circulating pump 6 through a transfer pipe 8 and sprayed into an absorbing column 1 from the spray nozzles 7 and falls therein. The absorbing soln. and gas to be treated are countercurrently brought into contact with each other and sulfur oxide in the gas is absorbed by the absorbing soln. 4 and the gas to be treated is subjected to desulfurization treatment. The absorbing soln. after desulfurization treatment falls within the absorbing column to be stored in the liquid storage tank 5. Air is blown in the absorbing soln. 4 from an air blow-in port 15 to oxidize the absorbing soln. (sulfite) after desulfurization treatment. Since a packed bed 14 of a packing material 13 is provided in the way of the absorbing soln. 4, air and the absorbing soln. are brought to a sufficient contact state and the oxidation reaction of sulfite can be accelerated even if much air is not used.

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、燃焼機器からの排ガス
等の被処理ガスを脱硫処理すると共に脱硫処理した吸収
液を酸化処理する吸収塔に関するものである。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to an absorption tower for desulfurizing a gas to be treated such as exhaust gas from a combustion device and oxidizing a desulfurized absorption liquid.

【0002】[0002]

【従来の技術】燃焼機器からの排ガス等の被処理ガス中
に含まれる硫黄酸化物を除去する装置の一つとして湿式
の排煙脱硫装置がある。
2. Description of the Related Art A wet flue gas desulfurization device is one of the devices for removing sulfur oxides contained in a gas to be treated such as exhaust gas from a combustion device.

【0003】この排煙脱硫装置は、吸収塔内で被処理ガ
スと炭酸カルシウム,水酸化マグネシウム等の吸収剤を
含むスラリ状の吸収液とを接触させて、被処理ガスの脱
硫処理を行うものである。吸収液は、吸収塔内下部の液
溜タンクに貯留され、この一部が塔内の上方に設けられ
たスプレーノズルから塔内に噴霧されて循環しつつ、塔
内を上昇する被処理ガスと気液接触して、ガス中の硫黄
酸化物が吸収液に吸収除去される。硫黄酸化物を吸収し
た吸収液(亜硫酸塩)は液溜タンクに落下して、一部が
酸化塔に移送されて酸化処理される。
This flue gas desulfurization apparatus performs desulfurization treatment of a gas to be treated by bringing the gas to be treated into contact with a slurry-like absorbing liquid containing an absorbent such as calcium carbonate or magnesium hydroxide in an absorption tower. Is. The absorption liquid is stored in a liquid storage tank in the lower part of the absorption tower, and a part of this is sprayed into the tower from a spray nozzle provided in the upper part of the tower and circulates while the gas to be treated rises in the tower. Upon contact with gas and liquid, the sulfur oxide in the gas is absorbed and removed by the absorbing liquid. The absorption liquid (sulfite) that has absorbed the sulfur oxides falls into the liquid storage tank, and a part of the absorption liquid is transferred to the oxidation tower for oxidation treatment.

【0004】[0004]

【発明が解決しようとする課題】ところで、前述の湿式
排煙脱硫装置では、排ガスを脱硫処理する吸収塔と、吸
収塔からの脱硫処理後の吸収液を酸化する酸化塔とを別
途設けていたので、設備費,運転費等のコストが高くな
る問題があった。
By the way, in the above-mentioned wet flue gas desulfurization apparatus, an absorption tower for desulfurizing exhaust gas and an oxidation tower for oxidizing the absorption liquid after desulfurization from the absorption tower are separately provided. Therefore, there is a problem that costs such as equipment cost and operation cost become high.

【0005】このため、図4及び図5に示すように、吸
収塔25の液溜タンク26内に空気吹込管27を配設し
て空気を直接吸収液中に吹き込み、吸収塔25内で脱硫
処理後の吸収液(亜硫酸塩)の酸化を行うことが考えら
れ、この際、吸収液に単に空気を吹き込むと、空気はそ
のまま吸収液中を上昇して液面に達するため、吸収塔2
5の液溜タンク26内に空気吹込管27を複数配設し、
これら吹込管27の長手方向に所定間隔を隔てて複数設
けられた吹出口28から空気を吹き出して、タンク26
(吸収液)全面に空気をほぼ均等に分散させることが提
案されている。しかし、吸収液全体に空気を吹き出すた
め、亜硫酸塩を酸化するには多量の空気が必要になり、
亜硫酸塩を効率よく酸化することができない。
For this reason, as shown in FIGS. 4 and 5, an air blowing pipe 27 is provided in the liquid reservoir tank 26 of the absorption tower 25 to blow air directly into the absorption liquid and desulfurize in the absorption tower 25. It is possible to oxidize the absorption liquid (sulfite) after the treatment. At this time, if air is simply blown into the absorption liquid, the air rises in the absorption liquid as it is and reaches the liquid surface.
A plurality of air blowing pipes 27 are arranged in the liquid storage tank 26 of No. 5,
Air is blown from a plurality of air outlets 28 provided at predetermined intervals in the longitudinal direction of these blow pipes 27, and the tank 26
(Absorbing liquid) It has been proposed to disperse air almost uniformly over the entire surface. However, since air is blown out to the whole absorption liquid, a large amount of air is required to oxidize sulfite,
Sulfite cannot be efficiently oxidized.

【0006】そこで、本発明は、このような実情に鑑み
なされたもので、その目的は、亜硫酸塩を効率よく酸化
することができる吸収塔を提供することにある。
Therefore, the present invention has been made in view of such circumstances, and an object thereof is to provide an absorption tower capable of efficiently oxidizing sulfite.

【0007】[0007]

【課題を解決するための手段】本発明は、前記目的を達
成するために、被処理ガス中の硫黄酸化物を吸収除去し
た吸収液を貯留する液溜タンクに空気を吹き込み亜硫酸
塩を酸化する吸収塔において、前記液溜タンクの吸収液
中に、気液接触を向上させるべく充填物を充填した充填
層を設けたものである。
In order to achieve the above-mentioned object, the present invention oxidizes sulfite by blowing air into a liquid storage tank which stores an absorbing liquid from which sulfur oxides in a gas to be treated are absorbed and removed. In the absorption tower, a packing layer filled with a packing material is provided in the absorption liquid of the liquid storage tank in order to improve gas-liquid contact.

【0008】[0008]

【作用】液溜タンクの吸収液中に充填層を設けたこと
で、空気は充填層を介して吸収液と十分に接触してから
液面に至るので、多量の空気を必要とせずに亜硫酸塩の
酸化反応が促進され、亜硫酸塩を効率よく酸化すること
が可能となる。
By providing the packed layer in the absorbent of the liquid storage tank, the air reaches the liquid surface after being sufficiently contacted with the absorbent through the packed layer, and therefore, a large amount of air is not required and sulfurous acid is not required. The oxidation reaction of the salt is promoted, and the sulfite can be efficiently oxidized.

【0009】[0009]

【実施例】以下、本発明の実施例を添付図面に基づいて
詳述する。
Embodiments of the present invention will be described below in detail with reference to the accompanying drawings.

【0010】図1において、1は燃焼機器例えばボイラ
からの排ガス(被処理ガス)を脱硫処理する排煙脱硫装
置の吸収塔を示し、この吸収塔1は例えば竪型の円筒状
に形成され、その側部下方に被処理ガスの導入口2が設
けられていると共に、上部に脱硫処理後のガスの排出口
3が設けられている。
In FIG. 1, reference numeral 1 denotes an absorption tower of a flue gas desulfurization apparatus for desulfurizing exhaust gas (gas to be treated) from a combustion device such as a boiler. The absorption tower 1 is formed in a vertical cylindrical shape, for example. An inlet 2 for the gas to be treated is provided on the lower side of the side portion, and an outlet 3 for the gas after desulfurization treatment is provided on the upper portion.

【0011】吸収塔1には、被処理ガス中の硫黄酸化物
の硫黄分を吸収するための炭酸カルシウム,水酸化マグ
ネシウム等の吸収剤が溶解されたスラリ状の吸収液を供
給する吸収液供給管4が接続されていると共に、その内
部下方には吸収液を溜める液溜タンク5が設けられてい
る。また、吸収塔1の液溜タンク5には、タンク5内の
吸収液の一部を循環ポンプ6により塔1内上方に設けら
れたスプレーノズル7に移送する移送管8が接続されて
おり、スプレーノズル7から噴霧された吸収液と塔1内
を上昇する排ガスとが向流気液接触してガス中の硫黄分
が吸収液に吸収除去され、被処理ガスが脱硫処理される
ようになっており、脱硫処理されたガスがエリミネータ
9を介してミストが除去されてから排出口3に導かれ
る。
The absorption tower 1 is supplied with an absorption solution in the form of a slurry in which an absorption agent such as calcium carbonate or magnesium hydroxide for absorbing the sulfur content of the sulfur oxide in the gas to be treated is dissolved. The pipe 4 is connected, and a liquid storage tank 5 for storing the absorbing liquid is provided below the inside thereof. A transfer pipe 8 is connected to the liquid storage tank 5 of the absorption tower 1 to transfer a part of the absorption liquid in the tank 5 to a spray nozzle 7 provided above the tower 1 by a circulation pump 6, The absorption liquid sprayed from the spray nozzle 7 and the exhaust gas rising in the tower 1 come into countercurrent gas-liquid contact to absorb and remove the sulfur content in the gas into the absorption liquid, so that the gas to be treated is desulfurized. Therefore, the desulfurized gas is guided to the discharge port 3 after the mist is removed via the eliminator 9.

【0012】さらに、吸収塔1の液溜タンク5内の下方
には、プロペラ状の側面式撹拌翼10が側壁近傍に設け
られている。撹拌翼10はその側壁を貫通して設けられ
たモータ11のシャフト12に取り付けられ、このシャ
フト12(撹拌翼10)の軸はタンク5の中心より所定
の角度ずれて配設され、モータ11の駆動により撹拌翼
10が回転して液中に吐出流が生じ、これにより円周方
向に水流が生じてタンク5内の吸収液が撹拌されるよう
になっている。
Further, below the inside of the liquid storage tank 5 of the absorption tower 1, a propeller-shaped side surface type stirring blade 10 is provided near the side wall. The stirring blade 10 is attached to a shaft 12 of a motor 11 provided through the side wall of the motor 11, and the shaft of the shaft 12 (stirring blade 10) is arranged with a predetermined angle offset from the center of the tank 5. The drive causes the stirring blade 10 to rotate to generate a discharge flow in the liquid, which causes a water flow in the circumferential direction to stir the absorbing liquid in the tank 5.

【0013】また、液溜タンク5の吸収液中には、充填
物13が充填されて気液接触を向上させる充填層14が
設けられている。充填物13は、気液接触を向上させる
ものであれば、球形、円筒形、ラシヒリング、レッシン
グリング、ベルルサドル等のどんなものでもよい。例え
ば球形のものは中空でもよく、直径は約20〜100mm にす
ることが好ましい。充填物13の材質は、吸収液より比
重が小さく、撹拌翼10による水流により移動し得る材
料で、例えばポリプロピレン,塩化ビニル等がある。こ
のように充填物はポリプロピレン等の吸収液より比重が
小さい材質で形成されているため、吸収液中に浮くの
で、充填物13を所定数浮かせれば液面から所定の距離
の充填層14が形成される。
Further, a filling layer 14 is provided in the absorption liquid of the liquid storage tank 5 to be filled with a filling 13 for improving gas-liquid contact. The packing 13 may be spherical, cylindrical, Raschig ring, Lessing ring, berl saddle, or the like as long as it improves gas-liquid contact. For example, the spherical shape may be hollow, and the diameter thereof is preferably about 20 to 100 mm. The material of the filler 13 is a material having a smaller specific gravity than the absorbing liquid and can be moved by the water flow of the stirring blade 10, and examples thereof include polypropylene and vinyl chloride. Since the filling material is formed of a material having a smaller specific gravity than the absorbing liquid such as polypropylene, it floats in the absorbing liquid. Therefore, if the filling material 13 is floated by a predetermined number, the filling layer 14 at a predetermined distance from the liquid surface is formed. It is formed.

【0014】充填層14の高さ(層厚)は、気液接触が
十分に行われるならば任意に決められる。例えば、吸収
塔1(液溜タンク5)の直径が10mで、タンク5の液面
の高さが約7〜8mの場合、充填層14の層厚は50〜10
0cm にすることが好ましい。これは、50cm未満であると
気液接触が十分に行われず、 100cmをこえて充填しても
著しい効率向上が期待できないからである。具体的な一
例としては、充填層14は、直径38mmのポリプロピレン
製の中空球(充填物)を液溜タンク5の吸収液中に液面
から約50cm充填して形成される。
The height (layer thickness) of the filling layer 14 is arbitrarily determined as long as gas-liquid contact is sufficiently performed. For example, when the diameter of the absorption tower 1 (liquid reservoir tank 5) is 10 m and the height of the liquid surface of the tank 5 is about 7 to 8 m, the layer thickness of the packed bed 14 is 50 to 10
It is preferably 0 cm. This is because if it is less than 50 cm, gas-liquid contact is not sufficiently performed, and if it exceeds 100 cm, a significant improvement in efficiency cannot be expected. As a specific example, the filling layer 14 is formed by filling polypropylene spheres (filling material) having a diameter of 38 mm with the absorbing liquid in the liquid storage tank 5 about 50 cm from the liquid surface.

【0015】さらに、液溜タンク5の充填層14の下方
には、その周方向に所定の間隔を隔てて空気吹込口15
が4つ以上設けられ、この空気吹込口15は、空気を接
線方向に吹き出すように形成されている。空気吹込口1
5は、吸収液に吹き込まれた空気が充填層14を介して
液面に至り、吸収液と十分に接触するので、例えば90°
間隔に4つ程度で十分である。
Further, below the filling layer 14 of the liquid storage tank 5, an air blowing port 15 is provided at a predetermined interval in the circumferential direction.
4 or more are provided, and the air blowing port 15 is formed so as to blow out air in a tangential direction. Air inlet 1
No. 5 is, for example, 90 ° because the air blown into the absorbing liquid reaches the liquid surface through the packed bed 14 and makes sufficient contact with the absorbing liquid.
About four intervals are sufficient.

【0016】次に本実施例の作用を述べる。Next, the operation of this embodiment will be described.

【0017】排ガス(被処理ガス)は、導入口2から吸
収塔1内に導入され、塔1内を上昇する。この吸収塔1
には、炭酸カルシウム等の吸収剤が溶解されたスラリ状
の吸収液が吸収液供給管4から導入され、液溜タンク5
内に溜まる。その一部が循環ポンプ6により移送管8を
介してスプレーノズル7に移送され、そのノズル7から
塔1内に噴霧落下する。この吸収液とガスとが向流接触
してガス中の硫黄酸化物が吸収液に吸収され、被処理ガ
スが脱硫処理される。脱硫処理されたガスは、エリミネ
ータ9を介してミストが除去されてから排出口3に至
り、そして他の系に導かれる。
Exhaust gas (gas to be treated) is introduced into the absorption tower 1 through the inlet 2 and rises in the tower 1. This absorption tower 1
A slurry-like absorbing liquid in which an absorbing agent such as calcium carbonate is dissolved is introduced into the liquid from the absorbing liquid supply pipe 4, and the liquid collecting tank 5
Accumulate inside. A part of it is transferred to the spray nozzle 7 through the transfer pipe 8 by the circulation pump 6, and sprayed and dropped from the nozzle 7 into the tower 1. The absorption liquid and the gas come into countercurrent contact with each other, the sulfur oxide in the gas is absorbed by the absorption liquid, and the gas to be treated is desulfurized. The desulfurized gas has its mist removed via the eliminator 9, reaches the discharge port 3, and is then introduced to another system.

【0018】脱硫処理後の吸収液は、塔1内を落下して
液溜タンク5に溜まる。この吸収液には空気吹込口15
から空気が吹き込まれ、脱硫処理後の吸収液(亜硫酸
塩)が酸化される。この際、吸収液中には充填物例えば
球形の充填物13が充填されて充填層14が設けられて
いるため、空気と吸収液とが十分接触するので、多量の
空気によらなくても亜硫酸塩の酸化反応を促進できる。
例えば、直径38mmのポリプロピレン製の中空球(充填
物)13を液溜タンク5の吸収液中に液面から約50cm充
填して充填層14を形成すると、接線方向に空気を吹き
込む空気吹込口15が4箇所程度でも、十分に空気と吸
収液とが接触する。また、タンク5全面に空気をほぼ均
等に分散させる場合に比して空気吹込口が少なくてすむ
ので、メンテナンスが容易となり、経済効果もある。
After the desulfurization treatment, the absorbing liquid drops in the tower 1 and collects in the liquid tank 5. This absorption liquid has an air inlet 15
Air is blown into the absorbent, and the desulfurized absorption liquid (sulfite) is oxidized. At this time, since the absorbing liquid is filled with the filling material, for example, the spherical filling material 13 and the filling layer 14 is provided, the air and the absorbing liquid are sufficiently in contact with each other. The salt oxidation reaction can be accelerated.
For example, when a polypropylene hollow sphere (filler) 13 having a diameter of 38 mm is filled in the absorbing liquid of the liquid storage tank 5 by about 50 cm from the liquid surface to form a filling layer 14, an air blowing port 15 for blowing air in a tangential direction. Even if there are about 4 points, the air and the absorbing solution are in sufficient contact. Further, since the number of air inlets is smaller than that in the case where the air is substantially evenly distributed over the entire surface of the tank 5, maintenance is facilitated and there is an economic effect.

【0019】さらに、撹拌翼10をモータ11により回
転駆動することにより、その翼10の背面(吸込側)の
液が翼の前方に押し出されて吐出流が生じ、タンク5内
に円周方向の水流が生じて吸収液が撹拌される。これに
より、空気を吸収液中に分散することができ、均一な酸
化反応の促進が図れる。また、吸収液中のSSの沈降防
止をも図れる。さらに、充填物13がポリプロピレン,
塩化ビニル等の吸収液より比重が小さい材質で形成され
ていると、充填物13は吸収液中に浮いているため、撹
拌翼10による水流により自由に動くため、空気の分散
がよくなると共に気液接触がより効果的になる。また、
固形分が充填物13の間に詰まることが抑制され、充填
層14での気液接触効果が十分に発揮される。
Further, when the stirring blade 10 is rotationally driven by the motor 11, the liquid on the back surface (suction side) of the blade 10 is pushed out in front of the blade to generate a discharge flow, and the discharge flow is generated in the tank 5 in the circumferential direction. A stream of water is created and the absorbent is stirred. As a result, air can be dispersed in the absorbing liquid, and uniform oxidation reaction can be promoted. Further, it is possible to prevent SS from settling in the absorbent. Further, the filler 13 is polypropylene,
When the filler 13 is made of a material having a smaller specific gravity than the absorbing liquid such as vinyl chloride, the filler 13 floats in the absorbing liquid, and is freely moved by the water flow by the stirring blades 10, so that the air dispersion is improved and the gas-liquid mixture is improved. The contact becomes more effective. Also,
The solid content is prevented from being clogged in the filling material 13, and the gas-liquid contact effect in the filling layer 14 is sufficiently exerted.

【0020】従って、吸収液中に充填層14を設けるこ
とにより、亜硫酸塩を効率よく酸化することができる。
Therefore, by providing the filling layer 14 in the absorbing liquid, the sulfite can be efficiently oxidized.

【0021】図2は前記第1の実施例の変形例を示す図
であり、前記実施例と異なるところは、吸収液中の任意
の所に充填層14を形成するようにした点である。すな
わち、図示するように、吸収液中の所定の位置に目開き
の荒い(充填物13が通過しない程度の)ネット例えば
金網16を張設し、この金網16の下に充填物13を充
填して充填層14を形成する。このように吸収液の中間
に充填層14を設けるようにしても、前記実施例とほぼ
同じ作用効果を奏し、脱硫処理した吸収液(亜硫酸塩)
を効率よく酸化することができる。充填層14の下部の
金網17は設けても設けなくてもどちらでもよいが、設
けることで水流等による充填物13の偏りを抑制するこ
とができる。
FIG. 2 is a diagram showing a modification of the first embodiment. The difference from the first embodiment is that the filling layer 14 is formed at an arbitrary position in the absorbent. That is, as shown in the drawing, a net (for example, a wire net 16) having a coarse mesh (to the extent that the filler 13 does not pass) is stretched at a predetermined position in the absorbent, and the filler 13 is filled under the wire net 16. To form the filling layer 14. Even if the packing layer 14 is provided in the middle of the absorbing solution as described above, the absorbing solution (sulfite) obtained by the desulfurization treatment has substantially the same function and effect as the above embodiment.
Can be efficiently oxidized. The wire net 17 below the filling layer 14 may or may not be provided, but by providing it, it is possible to suppress the bias of the filling 13 due to a water flow or the like.

【0022】図3は第2の実施例を示す図で、前記実施
例と異なるところは充填物18を吸収液より比重が大き
く、撹拌翼10による水流により移動し得る材料例えば
ガラスで形成する点である。すなわち、図示するよう
に、吸収液中の所定の位置に目開きの荒いネット例えば
金網19を張設し、この金網19の上にガラスの充填物
18を充填して充填層20を形成する。このように充填
層20を設けるようにしても、前記実施例とほぼ同じ作
用効果を奏し、亜硫酸塩を効率よく酸化することができ
る。また、充填層20の上部の金網21は設けても設け
なくてもどちらでもよいが、設けることで水流等による
充填物18の偏りを抑制することができる。
FIG. 3 is a view showing a second embodiment. The difference from the above-mentioned embodiment is that the filling material 18 has a specific gravity larger than that of the absorbing liquid and is made of a material such as glass which can be moved by the water flow of the stirring blade 10. Is. That is, as shown in the figure, a net having a coarse mesh, for example, a wire net 19 is stretched at a predetermined position in the absorbent, and a glass filler 18 is filled on the wire net 19 to form a filling layer 20. Even if the filling layer 20 is provided in this way, the same effects and advantages as in the above-described embodiment can be obtained, and the sulfite can be efficiently oxidized. Further, the wire net 21 above the filling layer 20 may or may not be provided, but by providing it, it is possible to suppress the bias of the filling material 18 due to a water flow or the like.

【0023】[0023]

【発明の効果】以上要するに本発明によれば、液溜タン
クの吸収液中に充填層を設けたので、亜硫酸塩を効率よ
く酸化できるという優れた効果を奏する。
In summary, according to the present invention, since the filling layer is provided in the absorbing liquid of the liquid storage tank, the excellent effect that the sulfite can be efficiently oxidized is obtained.

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

【図1】本発明の第1の実施例を示す構成図である。FIG. 1 is a configuration diagram showing a first embodiment of the present invention.

【図2】本発明の第1の実施例の変形例を示す構成図で
ある。
FIG. 2 is a configuration diagram showing a modification of the first embodiment of the present invention.

【図3】本発明の第2の実施例を示す構成図である。FIG. 3 is a configuration diagram showing a second embodiment of the present invention.

【図4】先に提案されている吸収塔の一例を示す構成図
である。
FIG. 4 is a configuration diagram showing an example of an absorption tower proposed previously.

【図5】図4中のA−A線矢視図である。5 is a view taken along the line AA in FIG.

【符号の説明】[Explanation of symbols]

5 液溜タンク 13 充填物 14 充填層 5 Liquid Storage Tank 13 Packing Material 14 Packing Bed

フロントページの続き (51)Int.Cl.6 識別記号 庁内整理番号 FI 技術表示箇所 B01D 53/34 ZAB B01D 53/34 125 D 125 E Continuation of the front page (51) Int.Cl. 6 Identification code Office reference number FI Technical display location B01D 53/34 ZAB B01D 53/34 125 D 125 E

Claims (1)

【特許請求の範囲】[Claims] 【請求項1】 被処理ガス中の硫黄酸化物を吸収除去し
た吸収液を貯留する液溜タンクに空気を吹き込み亜硫酸
塩を酸化する吸収塔において、前記液溜タンクの吸収液
中に、気液接触を向上させるべく充填物を充填した充填
層を設けたことを特徴とする吸収塔。
1. An absorption tower which oxidizes sulfite by injecting air into a liquid storage tank for storing an absorption liquid in which a sulfur oxide in a gas to be treated is absorbed and removed, and a gas-liquid mixture is contained in the absorption liquid in the liquid storage tank. An absorption tower provided with a packed bed filled with a packing material for improving contact.
JP6200717A 1994-08-25 1994-08-25 Absorbing column Pending JPH0857249A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP6200717A JPH0857249A (en) 1994-08-25 1994-08-25 Absorbing column

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP6200717A JPH0857249A (en) 1994-08-25 1994-08-25 Absorbing column

Publications (1)

Publication Number Publication Date
JPH0857249A true JPH0857249A (en) 1996-03-05

Family

ID=16429041

Family Applications (1)

Application Number Title Priority Date Filing Date
JP6200717A Pending JPH0857249A (en) 1994-08-25 1994-08-25 Absorbing column

Country Status (1)

Country Link
JP (1) JPH0857249A (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR100542953B1 (en) * 2000-10-04 2006-01-11 현대중공업 주식회사 Modified inlet part for the wet scrubber

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR100542953B1 (en) * 2000-10-04 2006-01-11 현대중공업 주식회사 Modified inlet part for the wet scrubber

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