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JPS6249931A - Refining device for waste gas - Google Patents

Refining device for waste gas

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Publication number
JPS6249931A
JPS6249931A JP60188205A JP18820585A JPS6249931A JP S6249931 A JPS6249931 A JP S6249931A JP 60188205 A JP60188205 A JP 60188205A JP 18820585 A JP18820585 A JP 18820585A JP S6249931 A JPS6249931 A JP S6249931A
Authority
JP
Japan
Prior art keywords
wall
column
gas
liquid
generator
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
JP60188205A
Other languages
Japanese (ja)
Inventor
Kenichi Nakagawa
健一 中川
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.)
Individual
Original Assignee
Individual
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 Individual filed Critical Individual
Priority to JP60188205A priority Critical patent/JPS6249931A/en
Publication of JPS6249931A publication Critical patent/JPS6249931A/en
Pending legal-status Critical Current

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

Abstract

PURPOSE:To remove fine liquid drops by providing a liquid drop generator to the lower part of a wetted wall column, suspending a cathode bar to the central part of the column and impressing a voltage to said bar and column in such a manner that the column wall acts as an anode thereby forming an electrostatic liquid drop separator. CONSTITUTION:Gas to be treated enters the column 1 from a gas duct 3a and is mixed with the liquid ejected from a water pipe 3b of a spray generator 3 provided in the lower part of the column in an injection part 3c. The mixture ascends in the form of the gas contg. the fine liquid drops in the column 1. THe voltage is impressed between the cathode bar 4 and the wetted wall 2 acting as the anode. The fine liquid drops charged negative is attracted in the state of contg. an acidic gas, dust, etc., to the wetted wall anode. An absorbent liquid is injected from an annular spray generator 5 provided in the upper part of the column to drop the liquid from the upper part of the wetted column, by which the gas absorption is further executed.

Description

【発明の詳細な説明】 産業上の利用分野: 本発明は、排ガスを、そのまま、または湿式ガス吸収装
置で断熱に近い状態で6理して酸性ガスの除去と除塵を
行−りた後、被処理ガスを過飽和状態(水蒸気で飽和さ
れた気体がざらに水の微滴を含んだ状態)にして、酸性
ガス・粉塵と含んだ微滴を核にした粒子成長を進行させ
、静電気液滴分離器により、微滴を除去することにより
排ガスを清浄化する装置に関する。同時除塵が行われる
ことは言うまでもない0 従来技術: 含硫黄燃料(中近東原油から得られる重油、その細石油
精製工場で生じる残渣油など)を燃焼すると、いわゆる
SO+cと煤などの粉塵を含んだ排ガスが生成する。こ
の排ガスを公知の湿式脱硫装置(充填床、泡鐘、網棚層
などを持ち、気液が向流接触するもの)で処理する際、
SO!ヲはじめ、Keg 、 NH,などの、水との反
応速度が大で、実質的に境界面への拡散が吸収速度を支
配する気体の場合には、速やかに除去可能である。しか
しながら、sosガスが微水滴へ溶解する場合、最初に
微水滴に溶解して生じた803ft含む微水滴は、その
粒子成長の速度が遅く、そのため、逃理済ガスを空中に
放出すると、育煙を生じ、さらに酸性雨の原因となって
いる。
[Detailed Description of the Invention] Industrial Application Field: The present invention processes exhaust gas as it is or in a near-insulated state using a wet gas absorption device to remove acid gas and remove dust. By bringing the gas to be treated into a supersaturated state (a state in which the gas saturated with water vapor contains fine droplets of water), particle growth is promoted using the fine droplets containing acid gas and dust as nuclei, and electrostatic droplets are generated. The present invention relates to a device for cleaning exhaust gas by removing fine droplets using a separator. It goes without saying that dust removal is carried out at the same time.0 Conventional technology: When sulfur-containing fuel (heavy oil obtained from Middle Eastern crude oil, residual oil produced at fine oil refineries, etc.) is burned, it contains so-called SO+C and dust such as soot. Exhaust gas is generated. When this exhaust gas is treated with a known wet desulfurization device (one that has a packed bed, a bubble bell, a net shelf layer, etc., and has gas and liquid in countercurrent contact),
SO! In the case of gases such as Keg, NH, etc., which have a high reaction rate with water and whose absorption rate is substantially dominated by diffusion to the interface, they can be quickly removed. However, when the SOS gas dissolves into microdroplets, the droplets containing 803ft formed by first dissolving into microdroplets have a slow particle growth rate, and therefore, when the escaped gas is released into the air, smoke growth occurs. This also causes acid rain.

しかしながら、その対策が確立されず、トラブルが続発
しているのは周知のと2#)である。
However, it is well known that no countermeasures have been established and troubles continue to occur.

解決しようとする問題点: 本発明は、特に排ガス中のS08を含む透液Miヲ除去
することを主目的とする。
Problems to be Solved: The main purpose of the present invention is to remove the permeate Mi containing S08 from the exhaust gas.

本発明者はSO,の除去方法を中心として同時に粉塵1
に除去する方法について種種研究を行った結果、S03
含有水滴は気体中の水蒸気を吸収し、また気体中を浮遊
する微水滴は相互間で結合と起こし大粒化するが、その
際液滴を構成する硫酸の濃度が下がると共に反応熱によ
り温度上昇し、その結果微滴の水蒸気圧が大VCなって
、水蒸気移動が起こり鑑くなり、そのため粒子成長速度
が遅延し、除去困難の原因になっていることを知った。
The present inventor has focused on a method for removing SO, and at the same time
As a result of conducting various research on methods of removing S03
Containing water droplets absorb water vapor in the gas, and small water droplets floating in the gas bond with each other and become larger, but at the same time the concentration of sulfuric acid that makes up the droplets decreases and the temperature rises due to the heat of reaction. It was learned that as a result, the water vapor pressure of the microdroplets becomes large VC, causing water vapor movement to occur, which delays the particle growth rate and causes difficulty in removal.

そして、被処理ガスを冷却すれば微滴も冷却され、被処
理ガスを過飽和にすれば、微滴の大型化が速やかに起こ
ること金知った。この条件下で、粉塵を核として水滴が
成長し、その除去が容易になることは言うまでもない。
I also learned that if the gas to be treated is cooled, the droplets will also be cooled, and if the gas to be treated is supersaturated, the size of the droplets will quickly increase. It goes without saying that under these conditions, water droplets grow with the dust as the core, making it easier to remove them.

問題を解決する手段: 本発明では、被処理ガスを過飽和にするため、ガス中に
直接液(水または水溶液で1令却されて低温であること
が望ましい。)を含ませる。微液滴を捕捉して成長した
含不純物液滴(不純物はSO8を主とする気体、粉塵で
代表される固体の少なくとも1)は、後で静電気液滴分
離器で除去する。
Means for Solving the Problem: In the present invention, in order to supersaturate the gas to be treated, a liquid (preferably at a low temperature by being quenched with water or an aqueous solution) is directly included in the gas. The impurity-containing droplets (the impurities are at least one of a gas mainly composed of SO8 and a solid represented by dust) that have grown by trapping the fine droplets are later removed by an electrostatic droplet separator.

本発明で、過飽和状態を作る液滴発生器としては、スプ
レー発生器(液をガス中に噴出さ、Cろ形式のものを言
う。)、または、エントレンメント発生器(液中にガス
をバブルさせ沸騰状態、(シて飛沫同伴を起こさせる形
式のものを言う。)を用いる。
In the present invention, the droplet generator for creating a supersaturated state is a spray generator (a type of C filtration system that spouts a liquid into a gas) or an entrainment generator (a type of droplet generator that blows gas into a liquid). A boiling state (meaning a type that causes droplet entrainment) is used.

しかして、過飽和状態を作る液滴発生装置と靜4気液滴
除去器とを、濡れ壁塔型ガス吸収塔内に、前者を下部、
後者を上部に配設し、静電気液滴除去器で捕捉された液
滴を、濡れ壁・1は伝って落下させ、濡れ養液を形成す
るのである。
Therefore, a droplet generator for creating a supersaturated state and a silent four-gas droplet remover are placed in a wet wall tower type gas absorption tower, with the former placed in the lower part.
The latter is disposed at the top, and droplets captured by the electrostatic droplet remover are caused to fall along the wetting wall 1 to form a wet nutrient solution.

また、必要に応じて、濡れ壁塔上部に、成金上方にスプ
レーする環状スプレー発生器を設置する。
Additionally, if necessary, an annular spray generator is installed at the top of the wet wall tower to spray onto the deposited metal.

多数基の濡れ壁塔τ、並列に使用するためには、四角井
桁構造、六角蜂巣構造の新面形状にし、隔壁の両面が濡
れ壁として働くようにする。
In order to use multiple wetted wall towers τ in parallel, new surface shapes such as a square well girder structure or a hexagonal honeycomb structure are used so that both sides of the partition walls function as wetted walls.

ナオ、SO2、NH,,1(ceナトノ吸収速度の速い
ガスは、S08が吸収される条件下では、完全に吸収で
さることは言うまでもなく、本発明は、事前に、これら
吸収速度の大きいガスを吸収除去すると否とに拘らず、
S03粉塵の除去を行い得る。
It goes without saying that gases with a high absorption rate are completely absorbed under the conditions in which S08 is absorbed. Regardless of whether it is absorbed or removed,
S03 dust removal may be performed.

作用: 過飽和状態はガス中に液体が分散した2相分散系でちっ
て、表面エネルギーが減少する方向すなわち、分散液が
凝縮する方向に不可逆変化が自然発生する。液粒子が小
さい場合、同一過飽和度(単位d横巾の液重量/蒸気重
竣)でも、液粒十数が多く、全表面積が大きい点で、粒
子成長に好都合であるが、一方コロイドのサイズに近づ
くにつれて、ブラウン運動が激しくなり、粒子衝突によ
る大t4化が困難になる。
Effect: A supersaturated state is a two-phase dispersion system in which a liquid is dispersed in a gas, and an irreversible change occurs spontaneously in the direction in which the surface energy decreases, that is, in the direction in which the dispersion liquid condenses. When the liquid particles are small, even at the same supersaturation degree (unit: d width of liquid weight/steam weight), there are many liquid particles and the total surface area is large, which is favorable for particle growth, but on the other hand, the size of the colloid As the value approaches , Brownian motion becomes more intense and it becomes difficult to increase t4 due to particle collisions.

ノズルから液を噴出させる場合、はとんどの部分が50
μm以上の粒子となり、いわゆるコロイドサイズの粒子
の含有はない。
When ejecting liquid from the nozzle, the most part is 50
The particles are larger than μm and do not contain so-called colloid-sized particles.

さて、燃焼排ガスの断熱飽和温度は、停泊50゛C以上
であり、湿式脱硫を行うと、SO8などを含んだ微水滴
がサスペンドした状態になる。
Now, the adiabatic saturation temperature of the combustion exhaust gas is 50°C or higher at berth, and when wet desulfurization is performed, fine water droplets containing SO8 etc. are suspended.

この排ガスは、ノズルから噴出した低温のスプレー状微
液調により冷却されて、過飽和となり、さらしζ微液滴
を′を成するが、これら微液滴は共存するSOaを含ん
だ微液滴またはスプレー状水滴ト結合して除徐に大滴化
するが、この際、スプレー水滴は比較的粒子径が大きい
ので(50−2000μ仇)、ガス中で微液滴より低速
運動et、、a液滴と衝突してその捕捉、したがってS
02などのガス吸収に貢献する。なお、周知のとおり、
小液滴の蒸気圧は、表面張力のため、大液滴の蒸気圧よ
り大でおるが(例えば、Moore : Physie
al Chemistry5 th Ed、 p、48
1tLOngman参照)、so、 2含んだ液滴は蒸
気圧が低く、そのため常に外部から蒸気・及収金行う状
態にあり、一般に808を含まぬ小滴の水蒸気圧が最大
で、次に808fc含まぬ大筒、その次に803を含む
水滴の順とな’)、5Ost−含む液滴のがス相金介し
ての大粒化が起こる。さらに、被処理ガスが不飽和の場
合、その中に含まれる液滴は蒸発して、湿球温度に近づ
くが、このため、液滴の粒径、終末速度が小になり被処
理ガスのと昇流で同伴し易くなる(空気中で、2m、1
00μm120μmの液滴の終末速度は、それぞれ、6
.8 m/sec、0.33m/see 、  1.2
1c4/seeであるo )。
This exhaust gas is cooled by the low-temperature spray-like liquid spray ejected from the nozzle, becomes supersaturated, and forms exposed ζ fine droplets, but these fine droplets contain coexisting SOa or fine liquid droplets. Sprayed water droplets combine and gradually become large droplets, but at this time, since the sprayed water droplets have a relatively large particle size (50-2000 μm), they move at a slower speed than fine droplets in the gas. Collisions with the drop and captures it, thus S
Contributes to the absorption of gases such as 02. Furthermore, as is well known,
The vapor pressure of a small droplet is higher than that of a large droplet due to surface tension (for example, Moore: Physie
al Chemistry5 th Ed, p, 48
1tLOngman), so, 2-containing droplets have a low vapor pressure, so they are always in a state of being steamed and collected from the outside.Generally, droplets that do not contain 808 have the highest water vapor pressure, followed by droplets that do not contain 808fc. The large tube is followed by the water droplet containing 803 ('), and the droplet containing 5Ost becomes larger through the phase metal. Furthermore, if the gas to be treated is unsaturated, the droplets contained therein will evaporate and approach the wet bulb temperature, which will reduce the particle size and terminal velocity of the droplets and reduce the temperature of the gas to be treated. It becomes easier to entrain due to rising current (in the air, 2 m, 1
The terminal velocity of a droplet of 00 μm and 120 μm is 6
.. 8 m/sec, 0.33 m/see, 1.2
1c4/see o).

静電気液滴分離器(至)は、前記スプレー発生装置の上
部に位置し、塔芯部に陰極棒(4)が懸垂し、塔壁が陽
極になるように電圧が印加され、負に荷電した液滴が塔
壁に移動しそこで放電する通常の構造になっているが、
塔壁で放電した液滴が、壁に溢って落下し濡れ壁を形成
する点に本発明の1特徴がある。濡れ壁は当然ながら、
濡れ壁塔としてガス吸収に貢献する。
The electrostatic droplet separator (to) is located at the top of the spray generator, and a cathode rod (4) is suspended from the column core, and a voltage is applied so that the column wall becomes an anode, making it negatively charged. It has a normal structure in which droplets move to the tower wall and discharge there,
One feature of the present invention is that droplets discharged on the tower wall overflow and fall onto the wall, forming a wet wall. Of course, wet walls
Contributes to gas absorption as a wet wall tower.

本発明において、必要により塔上部で、下向きに液をス
プレーする主な理由は、塔上部における濡れ養液の確保
のためで)す、他の理由は、スプレー自身によりガス吸
収・液滴結合を行わせること、さらには、静電気的に分
離される微液滴を供給することであって、充分な速度、
例えばIQm/sec以上で下方に噴出させて、上昇す
る被処理がスに微液滴をエンドレーンさせぬことが望ま
しい。
In the present invention, the main reason for spraying the liquid downward at the top of the tower as necessary is to secure a wet nutrient solution at the top of the tower.The other reason is to prevent gas absorption and droplet bonding by the spray itself. furthermore, providing electrostatically separated microdroplets at a sufficient rate,
For example, it is desirable to eject the liquid downward at a rate of IQm/sec or more so that the fine droplets do not end up in the rising process target.

実施例: A□図VCおいて、濡A lji塔(1)の濡れ壁(陽
鳳として慟ぐ。)(2)の内下部に、スプレー発生器(
3)が設けらルて2す、被処理ガスはガスダク)(:(
a)カら進入し、水管(3b)から噴出する液と、噴出
部(3C)において混合して、周知ウォータージェット
スクラバーなどの場合と同様に、微液滴を含んだガスと
なって、塔(1)内を上昇する。第2図はスプル−発生
器の構造の1例を示したもので、孔(3d)から彼処4
ガスの1部が吸入され、液微滴の生成に貢献している。
Example: In Figure VC, a spray generator (
3) is installed, and the gas to be treated is placed in a gas duct)(:(
a) The liquid enters from the water pipe (3b) and mixes with the liquid ejected from the water pipe (3b) at the ejection part (3C), forming a gas containing fine droplets, as in the case of well-known water jet scrubbers, etc. (1) Rise within. Figure 2 shows an example of the structure of a sprue generator.
A portion of the gas is inhaled and contributes to the formation of liquid droplets.

また第3図は、スプレー発生器のノズルの他の2例全示
したもつで、図の(&)は逆円錐体(ロ)に、下方の導
管(2)を上昇する液を衝突させ、(2)の外側を上昇
するガス中に微液滴を分散させる形式のもの、山)は液
導管(6)を上昇する液を僅故の小孔a3から噴出させ
、g外を上昇するガス中に微液滴を分散させる形式のも
のである。なp1飛床同伴の形で微液滴と作るエントレ
ンメント発生器の1例を第4図の下部に示す。図中被処
理ガスは導管翰から、多管濡れ壁塔(1)に導入され、
導管四から排出される。(2ga)、(2ob)、(2
Qc) 6どはL#立濡ル壁塔で断面四角形、断面六角
形となり、)4壁(2a)、(20)などt−−ル壁と
して隣接単位濡れ壁と共用する。碩は4・♂(イ)から
、多孔板−上に供給される。多孔板CAvよ、網、ター
ボグリッド、狭義の多孔板などを意味し、ガスが多孔板
を上昇する際、多数の気泡となり、板上の液体の飛沫を
同惨するようにガス速更を速くする(溢流堰r設けても
良いが、設ける必要はない。)。このように、エントレ
/メント発生器CID wi、多管濡れ壁塔に用いると
、各単位連れ壁塔にスプレー発生器を設置せずに済むの
で経済的である。
Fig. 3 also shows two other examples of spray generator nozzles, in which (&) in the figure impinges on the inverted cone (b) the liquid rising through the lower conduit (2); (2) is a type in which minute droplets are dispersed in the gas rising outside the pipe (6), and the liquid rising through the liquid conduit (6) is ejected from a small hole a3, and the gas rising outside g. This is a type of liquid in which fine droplets are dispersed. An example of an entrainment generator that generates microdroplets in the form of p1 flying bed entrainment is shown at the bottom of FIG. In the figure, the gas to be treated is introduced from the conduit into the multi-tube wet wall tower (1),
It is discharged from conduit 4. (2ga), (2ob), (2
Qc) 6 is an L# wetted wall tower with a square cross section and a hexagonal cross section, and is shared with the adjacent unit wetted wall as a t-le wall such as )4 walls (2a) and (20). The rice is fed from 4.♂(a) onto the perforated plate. Perforated plate CAv means net, turbo grid, perforated plate in a narrow sense, etc. When gas rises up the perforated plate, it forms many bubbles, which speeds up the gas velocity so as to cause the liquid to splash on the plate. (An overflow weir may be provided, but it is not necessary.) In this way, when the entrainment/mention generator CID wi is used in a multi-tube wet wall tower, it is economical because it is not necessary to install a spray generator in each unit wall tower.

繻れ壁塔内のガス上昇速度は5〜Q m/seeにとる
ことが、後続する静電気液滴分離器(ハ)との関係およ
び装置の効果的運転のために望ましく、この条件下で、
代表径211II以下のIfLmは彼処4ガスにエンド
レーンされる。
It is desirable that the gas rising rate in the cinnabar column be 5 to Q m/see for the relationship with the subsequent electrostatic droplet separator (c) and for effective operation of the device; under this condition,
IfLm with a representative diameter of 211II or less is end laned to 4 gases there.

第1図および第4図において、陰極棒(4)ハ、図示し
てない公知の高電圧発生器(モータージェネレーター、
水銀脩流器のM)により、濡れ壁(陽極)との間に数万
ボルトの電圧を印加され、そのため負に荷電した微液滴
は、酸性ガス、粉塵などを含んだ状標で、襦n壁・−極
に吸引され放電して被処理ガスから除去される。除去さ
れた液滴力mれ養液として濡れ壁を流れ落ち、TI4ル
壁塔電格てガス吸収に関与することは言うまでもない。
In FIGS. 1 and 4, a cathode rod (4) and a known high voltage generator (not shown) (motor generator,
A voltage of tens of thousands of volts is applied between the wetted wall (anode) by M) of the mercury flow device, and as a result, the negatively charged minute droplets are in a state containing acid gas, dust, etc. It is attracted to the n-wall/- pole, discharges, and is removed from the gas to be processed. Needless to say, the removed droplet force flows down the wetted wall as a nutrient solution and participates in gas absorption by the TI4 wall tower.

本発明は上記構成で、ウォータージェットスクラバー、
静電液滴分離器、覚れ電格として、いずれも勝れた性能
を示すが、さらに、塔上部から下向きに液をスプレーす
ることにより、塔上部の濡れ電液fp備加させ、6Ja
 n−i塔としての性能を大ならしめ、また、向流ウォ
ータージェットスクラバーとしての性能ヲ〃口えること
ができる。
The present invention has the above configuration, a water jet scrubber,
Both of them show excellent performance as an electrostatic droplet separator and a memorized electric rating, but in addition, by spraying the liquid downward from the top of the tower, a wet electrolytic liquid fp is prepared at the top of the tower.
The performance as a ni tower can be increased, and the performance as a countercurrent water jet scrubber can also be improved.

第1図または第4図の濡れ電格上部に設けられ、第5図
にその構造を例示した環状スプレー発生器(5)により
、吸収液をF方に向けて噴射し、濡れ壁上部から濡れ養
液を落下させ、かつ微液滴をF方にスプレーすることに
より、ガス精製効果が増加する。この際噴出速度を被処
理ガス上昇速度よシ大きくすることによシ、飛沫同伴上
はとんどなくすことができる。第5図に:虻いて(5a
)は環状液管で、液溜め(図示せず)から液が供給され
、スプレーノズル(5b)から液が噴出する。
An annular spray generator (5) installed at the top of the wetted electrical grid shown in Figure 1 or 4, the structure of which is illustrated in Figure 5, sprays the absorbent liquid in the direction F, spraying the wetting liquid from the top of the wetted wall. By dropping the nutrient solution and spraying fine droplets in the F direction, the gas purification effect is increased. At this time, entrainment of droplets can be almost completely eliminated by making the ejection speed greater than the rising speed of the gas to be treated. In Figure 5: Catfish (5a
) is an annular liquid pipe, to which liquid is supplied from a liquid reservoir (not shown), and liquid is ejected from a spray nozzle (5b).

第6図は多管濡れ電格cIQ(第4図)を単位濡れ電格
で構成するに際し、断面井桁状に単位濡れ電格を配列し
て隣接する塔壁を共用することでスペースと装置材料の
節約を図−りた1例で、別の実施例として断面が蜂巣形
六角形濡れ電格#を形成することにより、隔壁の両面を
濡れ壁苔壁として利用でき、同じ効果を得ることができ
ることは言うまでもない。(支)は液排出口である。
Figure 6 shows that when configuring the multi-pipe wetted electric grid cIQ (Figure 4) with unit wetted electric grids, the unit wetted electric grids are arranged in a parallel cross-sectional shape and the adjacent tower walls are shared, thereby saving space and equipment material. In another example, by forming a wetted electric grid with a honeycomb-shaped hexagonal cross section, both sides of the partition wall can be used as a wetted moss wall, and the same effect can be obtained. It goes without saying that it can be done. (support) is the liquid outlet.

発明の効果: 本発明は不純物を含む被処理排ガスを濡れ電格を用いて
除去するに際し、被処理ガス中に、吸収液の微滴を存在
せしめて酸性ガスを吸収し、また、冷却された低温の吸
収液fcI史用rることにより過飽和となし、微小粒子
の凝集粗大化作用により、大粒化させて、静電気液滴分
離器で分離する方法と、静電気液滴分離器により塔壁に
分離さルた液を濡れ養液として塔壁を流下させ、濡れ養
液として働かせる方法とを同−塔を用いて行わせるもの
であるから、2または3操作を単一装置で実施し得るこ
とになシ、プロセスの合理化と経済化に資するところが
大である。
Effects of the invention: When the present invention removes the exhaust gas containing impurities using a wet electric potential, the present invention allows minute droplets of an absorption liquid to be present in the gas to be treated to absorb the acidic gas, and The absorption liquid at low temperature becomes supersaturated by fcI history, and the particles are made into large particles by the agglomeration and coarsening action of the microparticles, and separated using an electrostatic droplet separator. Since the filtered liquid is made to flow down the column wall as a wet nutrient solution and is used as a wet nutrient solution using the same tower, two or three operations can be carried out in a single device. However, it greatly contributes to streamlining and economicalization of processes.

また、当然のことであるり;、除去効率が大となり、被
処理排ガスの高度の精製が可能である。
Moreover, as is obvious; the removal efficiency is increased, and the exhaust gas to be treated can be purified to a high degree.

かかる濡れ電格を四角井桁状配列、六角蜂巣状配列にす
ることにより、隣接する塔が、隔壁の両面を、それぞ几
、濡れ吹として利用でき、さらに経済的効果が増す。こ
の多管濡れ電格形式で、塔下部に設置する液滴発生器と
して、飛沫同伴現象を利用するエントレンメント発生器
を1基だけ設置して、彼処4排ガスに微水滴を含ませた
後に、各単位濡れ電格に配分すれば、さらにJA置の簡
略化・経済化を行い得る。
By arranging such wetted electrical grids in the form of square grids or hexagonal honeycombs, adjacent towers can use both sides of the bulkhead as a barrier and a wetting grid, respectively, further increasing the economic effect. In this multi-tube wet electric grid type, only one entrainment generator that utilizes the droplet entrainment phenomenon is installed as a droplet generator installed at the bottom of the tower. By allocating it to each unit wet voltage rating, the JA installation can be further simplified and made more economical.

さらに、単位濡れ電格の上部に、下向きのスプレー発生
器を配し、濡れ養液を増加させまたスプレーを増すこと
により精製効果はさらに増す。
In addition, a downward spray generator is placed above the unit wetted electric grid to increase the wetted nutrient solution and increase the amount of spray, thereby further increasing the purification effect.

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

第1図は、本発明の実施例の構成を示した支所面図であ
る。 第2図、第3図(a)、(b)はスプレー発生器の4造
を示す支所面図である。 第4図は、多管濡れ電格のド部に単一のエントレンメン
ト発生器を配し、各雪上部に環状スプレー発生器を設け
た。本発明の池の実施例の支所面図である。 第5図は、環状スプレー発生器を備えた濡n44塔上部
の鉱大図である。 第6図は、断面が四角井桁状の多彦濡れ電格の水平1f
r面図である。 (1)・・・、Jれ電格、(2)、(2a)、(2b)
 、(2e)・g し壁、(3)・・・スプレー発生器
、(4)・・・陰極陣、(5)・・・環状スプレー発生
器 (6)・・・逆円錐体、 (至)・・・小孔…・・・多
管濡ル電格、 (2)・・・エントレンメント発生器、磐・・・排ガス
入口、 (ホ)・・・排ガス出口、■・・・静電液滴分
離器、 4・・・液入口、  (ホ)・・・多孔板(至)・・・
液排出口 第1図 (a)        (b) 第3図 第5図     第6図
FIG. 1 is a branch plan view showing the configuration of an embodiment of the present invention. FIGS. 2, 3(a) and 3(b) are side views showing four structures of the spray generator. In FIG. 4, a single entrainment generator is placed at the bottom of a multi-pipe wetted electric grid, and an annular spray generator is provided above each snow. FIG. 3 is a branch plan view of an embodiment of the pond of the present invention. FIG. 5 is a diagram of the upper part of the wet N44 tower with an annular spray generator. Figure 6 shows the horizontal 1f of a Tahiko wet electric grid with a square well-shaped cross section.
It is an r-plane view. (1)..., J electric rating, (2), (2a), (2b)
, (2e)・g Wall, (3)...Spray generator, (4)...Cathode formation, (5)...Annular spray generator (6)...Inverted cone, (To )...Small hole...Multi-tube wetting electric rating, (2)...Entrainment generator, Rock...Exhaust gas inlet, (E)...Exhaust gas outlet, ■...Static electricity Droplet separator, 4...Liquid inlet, (E)...Perforated plate (to)...
Liquid outlet Fig. 1 (a) (b) Fig. 3 Fig. 5 Fig. 6

Claims (1)

【特許請求の範囲】 1 塔壁を濡れ壁液が落下し、被処理ガスが濡れ壁液と
向流に塔内を上昇する濡れ壁塔において該塔下部に、微
液滴を生成する液滴発生器が設置され、 該塔中芯部に、陰極棒が懸垂し、塔壁が陽極として作用
するよう、両極の間に電圧を印加し、静電液滴分離器を
形成せしめ、塔内を下方から上方に移動する被処理ガス
に微液滴を含ませた後に、該静電気液滴分離器で液滴を
分離することを特徴とする排ガスの精製装置。 2 液滴発生器がスプレー発生器である特許請求の範囲
第1項に記載の排ガスの精製装置。 3 液滴発生器が、エントレンメント発生器である特許
請求の範囲第1項に記載の排ガスの精製装置。 4 濡れ壁塔の上部に、液を下方にスプレーする環状ス
プレー発生器を設けた特許請求の範囲第1項から第3項
のいずれか1に記載の排ガスの精製装置。 5 複数基の断面四角形の濡れ壁塔が井桁状に塔壁を共
有し、該壁の両面がそれぞれ濡れ壁として働く特許請求
の範囲第1項から第4項のいずれか1に記載の排ガスの
精製装置。 6 複数基の断面六角形の濡れ壁塔が蜂巣状に塔壁を共
有し、該壁の両面がそれぞれ濡れ壁として働く特許請求
の範囲第1項から第4項のいずれか1に記載の排ガスの
精製装置。
[Scope of Claims] 1. Droplets that produce fine droplets at the bottom of a wetted wall tower in which a wetted wall liquid falls on the tower wall and the gas to be treated rises in the tower in a countercurrent to the wetted wall liquid. A generator is installed, a cathode rod is suspended in the core of the column, and a voltage is applied between the two electrodes so that the column wall acts as an anode, forming an electrostatic droplet separator and causing the inside of the column to flow. An exhaust gas purification device characterized in that after a gas to be treated moving from below to above contains minute droplets, the droplets are separated by the electrostatic droplet separator. 2. The exhaust gas purification device according to claim 1, wherein the droplet generator is a spray generator. 3. The exhaust gas purification device according to claim 1, wherein the droplet generator is an entrainment generator. 4. The exhaust gas purification device according to any one of claims 1 to 3, wherein an annular spray generator for spraying liquid downward is provided at the top of the wet wall column. 5. A waste gas exhaust system according to any one of claims 1 to 4, in which a plurality of wet wall towers with a square cross section share a tower wall in a cross-section shape, and both surfaces of the walls each act as a wet wall. Purification equipment. 6. The exhaust gas according to any one of claims 1 to 4, in which a plurality of wetted wall towers having a hexagonal cross section share a tower wall in a honeycomb manner, and both surfaces of the walls each act as a wetted wall. purification equipment.
JP60188205A 1985-08-26 1985-08-26 Refining device for waste gas Pending JPS6249931A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP60188205A JPS6249931A (en) 1985-08-26 1985-08-26 Refining device for waste gas

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP60188205A JPS6249931A (en) 1985-08-26 1985-08-26 Refining device for waste gas

Publications (1)

Publication Number Publication Date
JPS6249931A true JPS6249931A (en) 1987-03-04

Family

ID=16219609

Family Applications (1)

Application Number Title Priority Date Filing Date
JP60188205A Pending JPS6249931A (en) 1985-08-26 1985-08-26 Refining device for waste gas

Country Status (1)

Country Link
JP (1) JPS6249931A (en)

Cited By (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH02203915A (en) * 1989-02-02 1990-08-13 Morikawa Sangyo Kk Method and apparatus for gas recovery
EP0815921A1 (en) * 1996-07-05 1998-01-07 F-Tec Indus S.A. Method for treating exhaust gases
JP2008086994A (en) * 2007-10-29 2008-04-17 Akira Kijihana Wet exhaust gas treating device
JP2009519127A (en) * 2005-12-14 2009-05-14 アトキンズ リミテッド Extraction device
JP2009108848A (en) * 2007-10-30 2009-05-21 General Electric Co <Ge> System for recirculating exhaust gas of turbomachine
JP2015202485A (en) * 2014-04-16 2015-11-16 古河産機システムズ株式会社 Wet electric dust collector
JP2019051101A (en) * 2017-09-15 2019-04-04 アイシン精機株式会社 Deodorizing device

Citations (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS51132172A (en) * 1975-05-14 1976-11-17 Hitachi Ltd A process and apparatus for purification of exhaust gas

Patent Citations (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS51132172A (en) * 1975-05-14 1976-11-17 Hitachi Ltd A process and apparatus for purification of exhaust gas

Cited By (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH02203915A (en) * 1989-02-02 1990-08-13 Morikawa Sangyo Kk Method and apparatus for gas recovery
EP0815921A1 (en) * 1996-07-05 1998-01-07 F-Tec Indus S.A. Method for treating exhaust gases
FR2750616A1 (en) * 1996-07-05 1998-01-09 F Tec Indus PROCESS FOR TREATING GASEOUS EFFLUENTS BY ELECTROCHEMICAL PATHWAY
JP2009519127A (en) * 2005-12-14 2009-05-14 アトキンズ リミテッド Extraction device
JP2008086994A (en) * 2007-10-29 2008-04-17 Akira Kijihana Wet exhaust gas treating device
JP2009108848A (en) * 2007-10-30 2009-05-21 General Electric Co <Ge> System for recirculating exhaust gas of turbomachine
JP2015202485A (en) * 2014-04-16 2015-11-16 古河産機システムズ株式会社 Wet electric dust collector
JP2019051101A (en) * 2017-09-15 2019-04-04 アイシン精機株式会社 Deodorizing device

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