JPH0957054A - Dust-charging wet desulfurizer - Google Patents

Dust-charging wet desulfurizer

Info

Publication number
JPH0957054A
JPH0957054A JP21709695A JP21709695A JPH0957054A JP H0957054 A JPH0957054 A JP H0957054A JP 21709695 A JP21709695 A JP 21709695A JP 21709695 A JP21709695 A JP 21709695A JP H0957054 A JPH0957054 A JP H0957054A
Authority
JP
Japan
Prior art keywords
exhaust gas
mist
dust
collecting plate
charged
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Granted
Application number
JP21709695A
Other languages
Japanese (ja)
Other versions
JP3537553B2 (en
Inventor
Takeyoshi Yokosuka
丈由 横須賀
Takeo Komuro
武勇 小室
Norio Arashi
紀夫 嵐
Kensho Taniguchi
憲昭 谷口
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.)
Mitsubishi Power Ltd
Original Assignee
Babcock Hitachi KK
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 Babcock Hitachi KK filed Critical Babcock Hitachi KK
Priority to JP21709695A priority Critical patent/JP3537553B2/en
Publication of JPH0957054A publication Critical patent/JPH0957054A/en
Application granted granted Critical
Publication of JP3537553B2 publication Critical patent/JP3537553B2/en
Anticipated expiration legal-status Critical
Expired - Fee Related legal-status Critical Current

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  • Treating Waste Gases (AREA)
  • Electrostatic Separation (AREA)

Abstract

PROBLEM TO BE SOLVED: To efficiently remove the soot and dust in a waste gas and to prevent the generation of visible smoke by effectively utilizing a mist eliminator at the waste gas outlet of the absorption tower of the wet desulfurizer. SOLUTION: A demister 8 set close to the waste gas outlet of a desulfurizer is allowed to act also an electrostatic precipitator. A charging region consisting of a discharge-electrode wire 15 and a grounded electrode plate 19 is provided in a duct 28 between the outlet 27 for the waste gas treated in a desulfurizing and absorbing tower and the demister 8. A gap is furnished between the charging region and demister 8, and a mist collecting plate 22 and a cleaning spray 11 are set in the gap. The mist collecting plate 22 is connected to the grounded electrode plate 19 through a conductor or it is not connected to the grounded plate 19 through the conductor and the parallel mist collecting plates 22 are positively and negatively charged by turns. Further, a part or the whole of the cleaning soln. is periodically supplied to the absorption tower of the wet desulfurizer as makeup water.

Description

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

【0001】[0001]

【発明の属する技術分野】本発明は、ミストエリミネー
タを含む湿式脱硫装置において、ボイラーや加熱炉等か
ら排出される煤塵を電気的に、詳しくはコロナ放電を用
いて除去する集塵方法に関する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a dust collecting method for electrically removing dust discharged from a boiler, a heating furnace or the like electrically in a wet desulfurization apparatus including a mist eliminator, more specifically, using corona discharge.

【0002】[0002]

【従来の技術】石炭焚ボイラーや加熱炉等からの排ガス
中には、煤塵(ダスト)が多量に含まれており大気放出
前に各種脱塵装置により除去されている。その有力な脱
塵装置として、コロナ放電を利用した電気集塵機が挙げ
られる。この装置は、ガス流路中に放電電極と集塵電極
を有し、放電電極に負極性直流高電圧を荷電し、集塵電
極を接地することにより両電極間にコロナ放電を発生さ
せ、両電極間を通過する排ガス中の煤塵粒子に荷電を与
え、クーロン力により煤塵を排ガス中より分離するもの
であり、煤塵の除去には極めて効果的である。
Exhaust gas from coal-fired boilers, heating furnaces, etc. contains a large amount of soot and dust, which is removed by various dedusting devices before being released into the atmosphere. An electric dust collector that uses corona discharge is an example of a powerful dust removing device. This device has a discharge electrode and a dust collecting electrode in the gas flow path, charges the discharge electrode with a negative DC high voltage, and grounds the dust collecting electrode to generate corona discharge between the two electrodes. The dust particles in the exhaust gas passing between the electrodes are charged, and the dust particles are separated from the exhaust gas by the Coulomb force, which is extremely effective in removing the dust particles.

【0003】上記電気集塵機は集塵電極に付着した煤塵
を除去する仕方で乾式と湿式に分けられる。乾式電気集
塵機は集塵電極表面に付着した煤塵粒子(ダスト)を集
塵電極を槌打することで下部ホッパーにふるい落してい
る。一方、集塵電極表面を多量の流水で洗浄し、集塵電
極に付着した煤塵粒子を洗い流すものが湿式電気集塵機
である。
The electrostatic precipitator is classified into a dry type and a wet type according to a method of removing soot dust adhering to the dust collecting electrode. In a dry electrostatic precipitator, soot particles (dust) adhering to the surface of the dust collecting electrode are hammered to the dust collecting electrode, and are sifted to the lower hopper. On the other hand, a wet electrostatic precipitator is one in which the surface of the dust collecting electrode is washed with a large amount of running water to wash away the dust particles adhering to the dust collecting electrode.

【0004】近年、大気環境保全の立場から排出ダスト
量の規制が強化される傾向がある。また、現状の湿式電
気集塵機では捕集しきれないサブミクロン粒子(粒径
0.1〜1.0μm)のために、排ガスが大気放出され
た後、光撹乱を起こし可視化される可視煙が発生するこ
とが問題になっている。このため、排煙の脱塵能力の向
上が必要となった。しかし、脱塵装置の性能向上には限
界があり、排ガス処理システム全体としての脱塵効率の
向上が考えられている。例えば、脱塵効率向上システム
として、乾式電気集塵機をガス流れ上流側に設置し、先
ずダストを除去した後、脱硫装置を通過してガス温度が
低下した時点で、湿式電気集塵機やバグフィルターを設
置して二度目のダスト除去を行って、大気放出ダスト量
を減少させる方法が一般に考えられている。
In recent years, regulations on the amount of discharged dust tend to be tightened from the standpoint of environmental protection. In addition, due to submicron particles (particle size 0.1-1.0 μm) that cannot be collected by the current wet electrostatic precipitator, visible smoke is generated due to light disturbance after emission of exhaust gas into the atmosphere. To do is a problem. For this reason, it was necessary to improve the dust removal capability of the flue gas. However, there is a limit to improving the performance of the dust removing device, and it is considered to improve the dust removing efficiency of the exhaust gas treatment system as a whole. For example, as a dust removal efficiency improvement system, a dry electrostatic precipitator was installed on the upstream side of the gas flow, and after removing dust, a wet electrostatic precipitator and a bag filter were installed when the gas temperature passed through the desulfurization equipment. It is generally considered that a second dust removal is performed to reduce the amount of dust emitted into the atmosphere.

【0005】図7に示す従来の石炭焚きボイラ排ガスの
浄化処理フローに示すように、ボイラ1より排気された
煤塵を含む排ガスは、まず乾式電気集塵機2を通過し、
ある程度の煤塵が除去された後、熱交換器3で吸熱さ
れ、次いで湿式脱硫装置4に導かれる。この脱硫装置4
の入口ガス温度は130℃程度であるが、脱硫装置吸収
塔内のスプレイ液滴と接触することにより、脱硫装置出
口ガス温度は55℃まで低下する。このため脱硫装置4
の出口の排ガスには、温度55℃の飽和水蒸気が含まれ
ることになる。湿式脱硫装置吸収塔内では排ガスに脱硫
吸収液を向流にスプレイすることにより亜硫酸ガスを吸
収液に吸収除去させる。次いで排ガスは脱硫装置後流に
配置された湿式電気集塵機6に送られ、排ガス中のダス
トはさらに除去され、処理排ガスは、熱交換器3で10
0℃に再加熱され、蒸気による白煙を防止した後、煙突
7から排気される。
As shown in the conventional purification process flow of the coal-fired boiler exhaust gas shown in FIG. 7, the exhaust gas containing the soot dust exhausted from the boiler 1 first passes through the dry type electrostatic precipitator 2.
After removing a certain amount of soot and dust, the heat is absorbed by the heat exchanger 3 and then guided to the wet desulfurization device 4. This desulfurization equipment 4
Has an inlet gas temperature of about 130 ° C., but the contact with the spray droplets in the desulfurization device absorption tower lowers the desulfurization device outlet gas temperature to 55 ° C. Therefore, the desulfurization device 4
The exhaust gas at the outlet of the above contains saturated steam having a temperature of 55 ° C. In the wet desulfurization apparatus absorption tower, the desulfurization absorption liquid is sprayed countercurrently to the exhaust gas to absorb and remove sulfur dioxide gas into the absorption liquid. Next, the exhaust gas is sent to the wet electrostatic precipitator 6 arranged downstream of the desulfurization device, the dust in the exhaust gas is further removed, and the treated exhaust gas is heated by the heat exchanger 3 to 10
After being reheated to 0 ° C. to prevent white smoke due to steam, it is exhausted from the chimney 7.

【0006】このような乾式電気集塵機2をガス流れ上
流側に設置し、脱硫装置4の後流に湿式電気集塵機6を
設置する方法は、特公平06一38926号などに見る
ことができる。
A method of installing such a dry type electrostatic precipitator 2 on the upstream side of the gas flow and installing a wet type electrostatic precipitator 6 in the downstream of the desulfurization device 4 can be found in Japanese Patent Publication No. 06-138926.

【0007】[0007]

【発明が解決しようとする課題】ところで、湿式脱硫装
置の吸収塔内部では排ガスと吸収液を向流に接触させ
て、排ガス中の硫黄酸化物(SO2)を除去している。
その際、細かな吸収液液滴(吸収液ミスト)がガス流に
同伴されるため、この吸収液ミストを湿式脱硫装置吸収
塔排ガス出口近傍においてミストエリミネータを設置し
て除去しているのが一般である。通常排ガスは脱硫装置
吸収塔下部の入口から供給し、脱硫装置吸収塔上部の出
口から排出されるため、ミストエリミネータは吸収塔上
部近傍に設置される。湿式電気集塵機を設置する場合も
ミスト捕集のためミストエリミネータを設置する必要が
あるので、わざわざダクトをこのミストエリミネータ処
理排ガス出口から地面に設置してある湿式電気集塵機ま
で配管する必要があった。
By the way, inside the absorption tower of the wet desulfurization apparatus, the exhaust gas and the absorption liquid are brought into contact with each other in a countercurrent to remove the sulfur oxide (SO 2 ) from the exhaust gas.
At that time, since fine absorbing liquid droplets (absorbing liquid mist) are entrained in the gas flow, it is common to remove this absorbing liquid mist by installing a mist eliminator near the exhaust gas outlet of the absorption tower of the wet desulfurization device. Is. Normally, the exhaust gas is supplied from the inlet at the lower part of the absorption tower of the desulfurization device and discharged from the outlet at the upper part of the absorption tower of the desulfurization device, so that the mist eliminator is installed near the upper part of the absorption tower. Even when a wet electrostatic precipitator is installed, it is necessary to install a mist eliminator for collecting mist, so it was necessary to pipe a duct from the mist eliminator treatment exhaust gas outlet to the wet electrostatic precipitator installed on the ground.

【0008】このため、既設の排ガス処理プラントに対
して湿式電気集塵機を追設しようとする場合、新たに複
雑なダクト配管を設置する必要がある。また、湿式電気
集塵機本体の設置は、その重量から考えて地面に設置す
る必要があり、既設プラントの地面スペースの不足によ
り設置不可能の場合がある。
Therefore, when a wet electrostatic precipitator is to be additionally installed in an existing exhaust gas treatment plant, it is necessary to newly install a complicated duct pipe. Further, the wet electrostatic precipitator main body needs to be installed on the ground in consideration of its weight, and it may not be possible to install it due to lack of ground space in the existing plant.

【0009】従って、既設プラントの限られたスペース
を利用し、比較的低コストで高効率の脱塵を行える排煙
脱塵システムの開発が望まれている。
Therefore, there is a demand for development of a flue gas dedusting system which utilizes the limited space of an existing plant and is capable of highly efficient dust removal at a relatively low cost.

【0010】本発明の課題は、湿式脱硫装置の吸収塔排
ガス出口のミストエリミネータが配置されている排ガス
ダクト部分を有効に利用することによって、効率的に排
ガス中の煤塵を除去し、かつ可視煙の発生を防止するこ
とにある。
An object of the present invention is to effectively utilize the exhaust gas duct portion where the mist eliminator at the exhaust gas outlet of the absorption tower of the wet desulfurization device is arranged to efficiently remove the soot dust in the exhaust gas and to make visible smoke. To prevent the occurrence of.

【0011】[0011]

【課題を解決するための手段】本発明の上記目的は次の
構成によって達成される。すなわち、処理排ガス出口の
排ガスダクトの終端部にミストエリミネータを有する湿
式脱硫吸収塔において、該湿式脱硫吸収塔排ガス出口の
排ガスダクト内のミストエリミネータ上流側に放電電極
と接地電極とを含む荷電域を具備し、かつ、ミストエリ
ミネータ内に設けられるミスト捕集板と排ガスダクトと
の接合部位を電気的に絶縁し、該ミスト捕集板と該荷電
域接地電極とを導体で結合したダスト荷電湿式脱硫装
置、または、処理排ガス出口の排ガスダクトの終端部に
ミストエリミネータを有する湿式脱硫吸収塔において、
該湿式脱硫吸収塔排ガス出口の排ガスダクト内のミスト
エリミネータ上流側に放電電極と接地電極とを含む荷電
域を具備し、かつ、ミストエリミネータ内に設けられる
並立する多数のミスト捕集板のひとつおきに正の電荷を
印加し、該ミスト捕集板に挟まれる、あるいは前記ミス
ト捕集板に隣接するミスト捕集板に負の電荷を印加する
ダスト荷電湿式脱硫装置である。
The above object of the present invention is achieved by the following constitution. That is, in a wet desulfurization absorption tower having a mist eliminator at the end of the exhaust gas duct of the treated exhaust gas outlet, in the wet desulfurization absorption tower exhaust gas duct of the exhaust gas outlet of the wet desulfurization absorber, a charging region including a discharge electrode and a ground electrode on the upstream side of the mist eliminator. A dust-charged wet desulfurization system in which the mist collecting plate provided in the mist eliminator is electrically insulated from the joint portion of the exhaust gas duct, and the mist collecting plate and the charge area ground electrode are connected by a conductor. Apparatus, or in a wet desulfurization absorption tower having a mist eliminator at the end of the exhaust gas duct of the treated exhaust gas outlet,
The wet desulfurization absorption tower exhaust gas outlet is provided with a charging area including a discharge electrode and a ground electrode on the upstream side of the mist eliminator in the exhaust gas duct, and every other one of a number of parallel mist collecting plates provided in the mist eliminator. Is a dust-charged wet desulfurization device for applying a positive charge to the mist collecting plate, or sandwiching the mist collecting plate or applying a negative charge to the mist collecting plate adjacent to the mist collecting plate.

【0012】上記ダスト荷電湿式脱硫装置において、放
電電極と接地電極とを含む荷電域での排ガスダクトの断
面積よりミスト捕集板が設けられるミストエリミネータ
部分の排ガスダクトの断面積を広げることにより、該荷
電域での排ガス流速よりも該ミストエリミネータ部での
排ガス流速を減少させた構成、また、接地電極間の導体
として、あるいは接地電極と同符号の接合導体に排ガス
ダクトを含む構成物導電部を利用する構成とすることも
できる。
In the above dust-charged wet desulfurization apparatus, by expanding the cross-sectional area of the exhaust gas duct of the mist eliminator portion where the mist collecting plate is provided from the cross-sectional area of the exhaust gas duct in the charging area including the discharge electrode and the ground electrode, A structure in which the exhaust gas flow velocity in the mist eliminator portion is reduced as compared with the exhaust gas flow velocity in the charging region, and a conductive portion of a component including an exhaust gas duct as a conductor between ground electrodes or in a joint conductor having the same sign as the ground electrode. It is also possible to use a configuration that uses.

【0013】本発明は、燃焼排ガス煙道の上流に乾式電
気集塵機を、下流に脱硫プラントを有し、この脱硫プラ
ント排ガス出口近傍に設置されたミストエリミネータに
電気集塵機の機能を付加することを特徴とするものであ
る。
The present invention is characterized in that a dry type electrostatic precipitator is provided upstream of the combustion exhaust gas flue and a desulfurization plant is provided downstream thereof, and the function of the electrostatic precipitator is added to the mist eliminator installed near the desulfurization plant exhaust gas outlet. It is what

【0014】脱硫吸収塔処理排ガス出口の排ガスダクト
内におけるミストエリミネータ上流側に放電電極と接地
電極より構成される荷電域を設ける。例えば、脱硫吸収
塔処理排ガス出口から水平方向に延びる排ガスダクト内
にミストや煤塵の滞留や堆積を防ぐために放電電極ワイ
ヤと接地電極板を垂直方向に延びるように配置し、各々
ケーシングとなるダクトとは、碍子で結合することで電
気的に絶縁する。
A charging zone composed of a discharge electrode and a ground electrode is provided on the upstream side of the mist eliminator in the exhaust gas duct at the exhaust gas outlet of the desulfurization absorption tower process. For example, the discharge electrode wire and the ground electrode plate are arranged so as to extend vertically in order to prevent the accumulation and accumulation of mist and dust in the exhaust gas duct that extends horizontally from the desulfurization absorption tower treatment exhaust gas outlet, and each becomes a casing duct. Are electrically insulated by connecting with an insulator.

【0015】この荷電域とミストエリミネータとの間に
間隙を設け、この間隙にミスト捕集板洗浄スプレイを設
置することが好ましい。この洗浄スプレイの供給液は、
湿式脱硫吸収液の補給水を用いる。補給水が少量である
ため連立するミスト捕集板の前面部全域に供給するため
に噴霧スプレイ域を順次変更して補給水供給を行なう。
It is preferable that a gap is provided between the charging area and the mist eliminator, and a mist collecting plate cleaning spray is installed in this gap. The supply of this cleaning spray is
Make-up water for the wet desulfurization absorbent is used. Since the amount of make-up water is small, in order to supply the whole area of the front surface of the mist collecting plates that are connected at the same time, the spray spray area is sequentially changed to supply the make-up water.

【0016】ミストエリミネータのミスト捕集板は上方
から見て波形形状の金属板で作製し、数十cm間隔で連
立させる。このミスト捕集板とケーシングダクトとは、
碍子で結合することで電気的に絶縁し、各々のミスト捕
集板は、前出の接地電極板と導体により結合する。又
は、ミスト捕集板は接地電極板と導体により結合させず
に、連立するミスト捕集板に正と負の電荷を交互に印加
する。
The mist collecting plate of the mist eliminator is made of a corrugated metal plate as viewed from above, and is made up of several tens of cm intervals. The mist collecting plate and the casing duct are
The mist collecting plate is electrically insulated by being connected with an insulator, and each mist collecting plate is connected to the above-mentioned ground electrode plate by a conductor. Alternatively, the mist collecting plate is not coupled to the ground electrode plate by a conductor, but positive and negative charges are alternately applied to the mist collecting plates that are continuous.

【0017】ミスト捕集板に捕集された煤塵及びミスト
を捕集板下流側に設けられた洗浄液溜めに送り、洗浄液
溜めの洗浄液の一部はミスト捕集板洗浄スプレイに送水
する。また、定期的にこの洗浄液の一部又は全量を湿式
脱硫吸収塔に補給水として送水する。
The soot dust and mist collected by the mist collecting plate are sent to the cleaning liquid reservoir provided on the downstream side of the collecting plate, and a part of the cleaning liquid in the cleaning liquid reservoir is sent to the mist collecting plate cleaning spray. In addition, a part or all of this cleaning liquid is periodically sent to the wet desulfurization absorption tower as make-up water.

【0018】本発明によれば、ミスト捕集板表面に湿式
脱硫吸収液ミストが衝突し、ミスト自身の水分により、
ミスト捕集板表面は常に濡れた状態になって板上を上方
から下方へと流れることになる。このため荷電域で荷電
された煤塵がミスト捕集板に慣性衝突あるいはクーロン
力により捕集されてもミスト捕集板上に堆積したり、再
飛散することを防ぐことが可能になる。また、少量では
あるが比較的不純物の少ない洗浄液や工水をミスト捕集
板のガス流れ上流部に吹き付けているので、ミスト中の
アルカリ分が滞留付着し、スラグが発生するのを防止で
きる。
According to the present invention, the wet desulfurization absorbing liquid mist collides with the surface of the mist collecting plate, and the water content of the mist itself causes
The surface of the mist collecting plate is always in a wet state and flows over the plate from the upper side to the lower side. Therefore, it becomes possible to prevent the soot dust charged in the charging area from accumulating on the mist collecting plate or re-scattering even if it is collected by inertial collision or Coulomb force on the mist collecting plate. Further, since a small amount of cleaning liquid or industrial water containing relatively few impurities is sprayed onto the gas flow upstream portion of the mist collecting plate, it is possible to prevent slag from accumulating and accumulating the alkali component in the mist.

【0019】これらの捕集ミストと捕集煤塵は洗浄液溜
めに送られた後、湿式脱硫吸収塔に補給水として送ら
れ、煤塵は脱硫装置の廃液と同時に処理されるので、独
自の固定処理を行なう必要が無い。
These collected mists and collected soot dusts are sent to the cleaning liquid reservoir and then sent as make-up water to the wet desulfurization absorption tower, and the soot dusts are treated at the same time as the waste liquid of the desulfurization device, so that a unique fixing treatment is required There is no need to do it.

【0020】また、荷電域とミスト捕集板との間に間隙
を設けることにより、荷電域を通過して荷電された飛行
煤塵が同じく飛行している荷電されなかった吸収液ミス
トや洗浄液ミストに付着するための時間を与えることに
なり、煤塵粒子単独よりも径が大きなミストと煤塵の結
合粒子を形成する。連立するミスト捕集板間をこれら結
合粒子が飛行することになるが、径が大きく、重いため
にガス流への同伴が抑えられ、主に慣性衝突によりミス
ト捕集板表面に効率良く付着回収されることになる。
Further, by providing a gap between the charging area and the mist collecting plate, the flying soot dust charged through the charging area is also charged to the uncharged absorbing solution mist or cleaning solution mist. This will give time for the particles to adhere, and form combined particles of mist and dust that are larger in diameter than the dust particles alone. These bound particles fly between the coalesced mist collecting plates, but because of their large diameter and heavy weight, their entrainment in the gas flow is suppressed, and they are efficiently attached and collected on the surface of the mist collecting plate mainly due to inertial collision. Will be done.

【0021】また、これらミストと結合しなかった荷電
煤塵もクーロン力によりミスト捕集板に付着除去され
る。このクーロン力を強めるために連立するミスト捕集
板に正と負の電荷を交互に印加する方法が有効であり、
こうすることによってミスト捕集板間には負から正方向
への電場が形成され、負に荷電した煤塵が正極のミスト
捕集板に押しつけられるように確実に捕集される。
Further, the charged soot and dust which have not been combined with these mists are also adhered and removed to the mist collecting plate by the Coulomb force. In order to strengthen this Coulomb force, it is effective to apply positive and negative charges alternately to the mist collecting plates that are in parallel.
By doing so, an electric field from the negative direction to the positive direction is formed between the mist collecting plates, and the negatively charged soot dust is reliably collected so as to be pressed against the mist collecting plate of the positive electrode.

【0022】その他の作用として、湿式脱硫吸収塔から
の飛散ミストが荷電域で電荷が付与されることにより、
クーロン力によりミスト捕集板により付着しやすくなる
ため、従来のミスト捕集域よりコンパクト化することが
可能である。
As another function, the scattered mist from the wet desulfurization absorption tower is charged with electric charges in the charging region,
The Coulomb force makes it easier for the mist collecting plate to adhere to the mist collecting plate, so that the mist collecting area can be made more compact.

【0023】[0023]

【発明の実施の形態】本発明の実施例を図面と共に説明
する。 実施例1 図4に本発明に適応した石炭焚ボイラプラントの排煙処
理装置の系統図を示す。ボイラ1より排気された煤塵を
含む排ガスは、まず乾式電気集塵機2を通過し、ある程
度の煤塵が除去された後、熱交換器3で吸熱され、次い
で湿式脱硫装置4に導かれる。この脱硫装置4の入口ガ
ス温度は130℃程度であるが、脱硫装置吸収塔内のス
プレイ液滴と接触することにより、脱硫装置出口ガス温
度は55℃まで低下する。このため脱硫装置4の出口の
排ガスには、温度55℃の飽和水蒸気が含まれることに
なる。湿式脱硫装置の吸収塔内では排ガスに対して脱硫
吸収液を向流にスプレイすることにより亜硫酸ガスを吸
収液に吸収除去しているが、スプレイされた脱硫吸収液
の径の小さいもの(吸収液ミスト)は排ガス流に同伴さ
れる。排ガス流に同伴される吸収液ミストの径は数μm
〜数千μmであり、ダストの径(0.1〜10μm)よ
り大きい。
DESCRIPTION OF THE PREFERRED EMBODIMENTS Embodiments of the present invention will be described with reference to the drawings. Example 1 FIG. 4 shows a system diagram of a flue gas treatment apparatus of a coal-fired boiler plant adapted to the present invention. Exhaust gas containing soot dust exhausted from the boiler 1 first passes through the dry electrostatic precipitator 2 to remove a certain amount of soot, and then is absorbed by the heat exchanger 3 and then guided to the wet desulfurization device 4. Although the inlet gas temperature of the desulfurizer 4 is about 130 ° C., the desulfurizer outlet gas temperature is lowered to 55 ° C. by coming into contact with the spray droplets in the desulfurizer absorber tower. Therefore, the exhaust gas at the outlet of the desulfurization device 4 contains saturated steam having a temperature of 55 ° C. In the absorption tower of the wet desulfurization device, the desulfurization absorption liquid is absorbed and removed by the countercurrent spraying of the desulfurization absorption liquid with respect to the exhaust gas. Mist) is entrained in the exhaust gas flow. The diameter of the absorbing liquid mist entrained in the exhaust gas flow is several μm
Is up to several thousand μm, which is larger than the diameter of dust (0.1 to 10 μm).

【0024】このミストとダストを含む排ガスは、吸収
塔出口直後のダクト内に設けられたミストエリミネータ
8の放電電極ワイヤ15と接地電極板19からなる荷電
域で効果的に荷電され、ミストエリミネータ8のミスト
捕集板22に慣性衝突により付着除去される。ダストを
除去された処理排ガスは、熱交換器3で100℃に再加
熱され、蒸気による白煙を防止した後、煙突7から排気
される。
The exhaust gas containing the mist and dust is effectively charged in the charging region consisting of the discharge electrode wire 15 and the ground electrode plate 19 of the mist eliminator 8 provided in the duct immediately after the outlet of the absorption tower, and the mist eliminator 8 is discharged. The mist collecting plate 22 is attached and removed by inertial collision. The treated exhaust gas from which dust has been removed is reheated to 100 ° C. by the heat exchanger 3 to prevent white smoke due to steam, and then exhausted from the chimney 7.

【0025】図3には図1のミストエリミネータ8部分
の上方からの断面視図を示し、図1及び図2にミストエ
リミネータ8を有する湿式脱硫吸収装置4に吸収塔排ガ
ス出口27からミストエリミネータ8の間に放電電極ワ
イヤ15と接地電極板19とからなる荷電域を設置した
装置の詳細図を示す。
FIG. 3 is a sectional view of the mist eliminator 8 portion of FIG. 1 from above, and FIGS. 1 and 2 show the wet desulfurization absorber 4 having the mist eliminator 8 from the absorption tower exhaust gas outlet 27 to the mist eliminator 8. A detailed view of an apparatus in which a charging area composed of a discharge electrode wire 15 and a ground electrode plate 19 is provided between the two is shown.

【0026】湿式脱硫吸収装置4の排ガス出口27から
下流域に金属板で出来た複数枚の接地電極板19が互い
に平行にガス流れに対して垂直方向に等間隔で配列され
るように、ケーシングダクト28に支持碍子21を介し
て支持されている。なお、接地電極板19の配列の仕方
はガス流速が大きくミストやダストの滞留が起こらない
場合はガス流れに対して垂直である必要は無く、また相
互に等間隔に配置する必要はない。
The casing is formed so that a plurality of ground electrode plates 19 made of metal plates are arranged in the downstream region from the exhaust gas outlet 27 of the wet desulfurization absorber 4 in parallel with each other at equal intervals in the direction perpendicular to the gas flow. It is supported by the duct 28 via the support insulator 21. The arrangement of the ground electrode plates 19 does not need to be perpendicular to the gas flow and does not need to be equidistant from each other when the gas flow velocity is large and the accumulation of mist or dust does not occur.

【0027】この平行に並んだ接地電極板19と接地電
極板19間の中央には各々放電電極ワイヤ15が張られ
ている。接地電極板19を挟んで近接する放電電極ワイ
ヤ15同士は導体結合しており、またケーシングダクト
28に支持碍子17で取り付けられている。このため排
ガス流れ方向の並びには全て電気的に導体のセクション
を形成している。同様の放電電気ワイヤ15と接地電極
板19のセクションが複数集まって荷電域が形成されて
いる。
Discharge electrode wires 15 are stretched at the centers between the ground electrode plates 19 arranged in parallel with each other. The discharge electrode wires 15 that are close to each other with the ground electrode plate 19 interposed therebetween are conductor-coupled to each other, and are attached to the casing duct 28 by the support insulator 17. For this reason, all the sections in the exhaust gas flow direction form electrically conductive sections. A plurality of similar sections of the discharge electric wire 15 and the ground electrode plate 19 are gathered to form a charging area.

【0028】一方、ミストエリミネータ8のミスト捕集
板22とケーシングダクト28は碍子23により結合
し、電気的に絶縁となっている。図2に示すように各々
のミスト捕集板22は導体で結合している。このミスト
捕集板22と接地電極板19は結合導体20により結合
し、その一端に接地線25が結合している。さらにこの
接地線25は、ケーシングダクト28と電気的に絶縁に
するための管状碍子24を介してケーシングダクト28
を貫通した接地線25により地表に接地している。
On the other hand, the mist collecting plate 22 of the mist eliminator 8 and the casing duct 28 are connected by an insulator 23 and are electrically insulated. As shown in FIG. 2, the mist collecting plates 22 are connected by a conductor. The mist collecting plate 22 and the ground electrode plate 19 are connected by a connecting conductor 20, and a ground wire 25 is connected to one end thereof. Further, the ground wire 25 is connected to the casing duct 28 through a tubular insulator 24 for electrically insulating the casing duct 28.
It is grounded to the surface of the earth by a grounding wire 25 penetrating through

【0029】高圧電源18から放電電極ワイヤ15には
負の電荷をかけ、接地電極板19には正の電荷をかけて
いる。このため接地電極板19と結合導体20により結
合した各々のミスト捕集板22も正の電荷がかかってい
ることになる。この放電電極ワイヤ15と接地電極板1
9との間に8kV/cmの高電圧をかけコロナ電界を形
成する。このコロナ電界が形成された荷電域を通過する
ガス流速は5m/s程度である。このため荷電域で理想
的な接触時間である0.036秒以上を実現する必要
上、有効荷電域の長さは18cm以上であることが望ま
しい。
A negative charge is applied to the discharge electrode wire 15 from the high voltage power source 18, and a positive charge is applied to the ground electrode plate 19. Therefore, each mist collecting plate 22 coupled by the ground electrode plate 19 and the coupling conductor 20 is also positively charged. The discharge electrode wire 15 and the ground electrode plate 1
A high voltage of 8 kV / cm is applied between 9 and 9 to form a corona electric field. The flow velocity of gas passing through the charged region where the corona electric field is formed is about 5 m / s. Therefore, in order to realize an ideal contact time of 0.036 seconds or more in the charging area, it is desirable that the length of the effective charging area is 18 cm or more.

【0030】湿式脱硫装置4の排ガス入口26から導入
される排ガスは吸収塔底部に設けられた吸収液溜めより
吸収液スプレ配管14を介して吸収液スプレノズル10
で噴霧される吸収液により脱硫処理される。脱硫処理の
後、排ガス中の煤塵及び吸収液ミストは、放電電極ワイ
ヤ15と接地電極板19からなる荷電域を通過する際、
負イオンが表面に付着するため負に帯電し、互いに反発
しあって周囲に広がりながら飛行を続けるが、あるもの
はパイプ12より供給される洗浄水をミスト捕集板洗浄
スプレイ11からミストに衝突させ、あるいはクーロン
力で引き付けられて結合して煤塵(ダスト)とミストの
結合物を形成する。この煤塵とミストの結合物は、ミス
ト捕集板22表面に慣性衝突することで捕集されるが、
ミスト捕集板22表面にはミスト自身の水分あるいは洗
浄水により水膜流が形成されているので、再飛散を起こ
すこと無くミスト捕集板22上を下方へと流れ落ち、捕
集板22下方に設けられた洗浄液溜め9に送られる。こ
れらミストと結合しなかった荷電煤塵においてもクーロ
ン力によりミスト捕集板22に付着し、前者同様洗浄液
溜め9まで流れ落ちる。
The exhaust gas introduced from the exhaust gas inlet 26 of the wet desulfurization apparatus 4 is absorbed by the absorbent spray nozzle 10 provided at the bottom of the absorption tower through the absorbent spray pipe 14.
Is desulfurized by the absorbing liquid sprayed in. After the desulfurization treatment, the soot dust and the absorbing liquid mist in the exhaust gas pass through the charged area composed of the discharge electrode wire 15 and the ground electrode plate 19,
Negative ions attach to the surface and are thus negatively charged, repel each other and continue flying while spreading to the surroundings, but some of them collide the cleaning water supplied from the pipe 12 from the mist collecting plate cleaning spray 11 to the mist. Or, they are attracted by the Coulomb force and combine with each other to form a combined product of dust and mist. The soot and mist combination is collected by inertial collision with the surface of the mist collecting plate 22,
Since a water film flow is formed on the surface of the mist collecting plate 22 due to the water content of the mist or the washing water, it flows down on the mist collecting plate 22 without re-scattering, and falls below the collecting plate 22. It is sent to the cleaning liquid reservoir 9 provided. The charged dust that has not been combined with these mists also adheres to the mist collecting plate 22 due to the Coulomb force and flows down to the cleaning liquid reservoir 9 as in the former case.

【0031】洗浄液溜め9の洗浄液の一部はミスト捕集
板洗浄スプレイ11にパイプ12を経由して送られる
が、定期的にこの洗浄液の一部又は全量を湿式脱硫吸収
装置4に送水管13を通り補給水として送られる。
A part of the cleaning liquid in the cleaning liquid reservoir 9 is sent to the mist collecting plate cleaning spray 11 via the pipe 12, and a part or the whole amount of this cleaning liquid is periodically supplied to the wet desulfurization absorber 4 by the water pipe 13. Will be sent as makeup water.

【0032】実施例2 図5に示す例は、図1及び図2に示したミストエリミネ
ータと同一の構成部材からなるが、相違点はケーシング
ダクト(図示せず)内に設ける放電電極ワイヤ15と接
地電極板19間に電圧を印加するのとは独立に、ミスト
捕集板22に高電圧を印加する方法である。
Example 2 The example shown in FIG. 5 comprises the same components as the mist eliminator shown in FIGS. 1 and 2, except that the discharge electrode wire 15 provided inside a casing duct (not shown) This is a method of applying a high voltage to the mist collecting plate 22 independently of applying a voltage between the ground electrode plates 19.

【0033】これにより、ミスト捕集板22部分でのク
ーロン力を高めることができる。図5に示す例は、連立
するミスト捕集板22に正と負の電荷を交互に印加して
いる。印加電圧は、荷電部同様8kV/cm程度とする
が、これらミスト捕集板22間には静電界が形成され
る。こうすることによって、ミスト捕集板22間には負
から正方向への電場が形成され、負に荷電した煤塵が正
極のミスト捕集板22に押しつけられるように確実に捕
集される。
As a result, the Coulomb force at the mist collecting plate 22 can be increased. In the example shown in FIG. 5, positive and negative charges are alternately applied to the mist collecting plates 22 that are continuous. The applied voltage is about 8 kV / cm as in the charging section, but an electrostatic field is formed between these mist collecting plates 22. By doing so, an electric field from the negative direction to the positive direction is formed between the mist collecting plates 22, and the negatively charged soot dust is reliably collected so as to be pressed against the mist collecting plate 22 of the positive electrode.

【0034】実施例3 本実施例は、荷電域電極上に吸収液ミスト及び荷電煤塵
が堆積するのを低減するために、図6に示すようにミス
トエリミネータのケーシングダクト28にはミスト捕集
板22のみを設け、ケーシングダクト28の断面積より
狭い上流部ダクト27内に放電電極ワイヤ15と接地電
極板19を設けた荷電域を設置したものである。
Embodiment 3 In this embodiment, in order to reduce the accumulation of absorbing liquid mist and charged dust on the charge area electrode, a mist collecting plate is provided in the casing duct 28 of the mist eliminator as shown in FIG. 22 is provided, and the charging area provided with the discharge electrode wire 15 and the ground electrode plate 19 is provided in the upstream duct 27 that is narrower than the cross-sectional area of the casing duct 28.

【0035】断面積が比較的狭いダクト27を通過する
排ガスはその通過速度が増加するので、電極15、19
表面に付着した吸収液ミスト及び荷電煤塵を吹き飛ばす
ことが有効に行える。
Exhaust gas passing through the duct 27 having a relatively narrow cross-sectional area increases its passage speed, so that the electrodes 15, 19 are
It is possible to effectively blow off the absorbing solution mist and charged soot dust adhering to the surface.

【0036】上記実施例1から実施例3で用いた接地電
極19間の導体として、あるいは接地電極と同符号の接
合導体20の代わりに、ダクト27、28の本体を含む
構成物導電部を利用しても一向に差し支えない。
As a conductor between the ground electrodes 19 used in the first to third embodiments, or instead of the joint conductor 20 having the same sign as the ground electrode, a constituent conductive portion including the bodies of the ducts 27 and 28 is used. But it doesn't matter.

【0037】[0037]

【発明の効果】本発明を用いることにより、脱硫プラン
トの出口においてコロナ放電により荷電された排ガス中
の煤塵が効率良く除去されることになり、大気放出煤塵
量が減少して、可視煙の防止が可能である。同時に既設
脱硫プラントを僅かに改良するだけなのでコスト増加を
きたすことがない。
EFFECTS OF THE INVENTION By using the present invention, the soot dust in the exhaust gas charged by corona discharge can be efficiently removed at the outlet of the desulfurization plant, the amount of soot emitted to the atmosphere is reduced, and the visible smoke is prevented. Is possible. At the same time, the existing desulfurization plant is only slightly improved so that the cost does not increase.

【0038】また、集塵電極であるミスト捕集板は常に
ミストや脱硫装置補給水により、洗浄されているため
に、集塵電極(ミスト捕集板)上に付着したダストの再
飛散を防げ、かつ、新たに水洗設備を設置する必要がな
い。その他、ダストはミスト捕集板洗浄液に回収された
後、脱硫補給水として供給されるため特別な煤塵固定設
備を設ける必要がない。このため既存スペースを有効に
利用することが可能である。
Further, since the mist collecting plate, which is the dust collecting electrode, is always washed with mist or desulfurization device make-up water, re-scattering of dust adhering on the dust collecting electrode (mist collecting plate) can be prevented. Moreover, it is not necessary to newly install a washing facility. In addition, since the dust is collected by the mist collecting plate cleaning liquid and then supplied as desulfurization make-up water, it is not necessary to install a special soot and dust fixing facility. Therefore, it is possible to effectively use the existing space.

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

【図1】 本発明の一実施例のダスト荷電湿式脱硫装置
の吸収塔部分を示す。
FIG. 1 shows an absorption tower portion of a dust-charged wet desulfurization apparatus according to an embodiment of the present invention.

【図2】 本発明の一実施例のダスト荷電湿式脱硫装置
のミストエリミネータ部分の斜視図を示す。
FIG. 2 is a perspective view of a mist eliminator portion of a dust-charged wet desulfurization apparatus according to an embodiment of the present invention.

【図3】 本発明の一実施例のダスト荷電湿式脱硫装置
のミストエリミネータ部分の構成図を示す。
FIG. 3 is a configuration diagram of a mist eliminator portion of a dust-charged wet desulfurization apparatus according to an embodiment of the present invention.

【図4】 本発明の一実施例のダスト荷電湿式脱硫装置
が適用されるボイラ排ガスの浄化処理装置フローを示
す。
FIG. 4 shows a flow chart of a boiler exhaust gas purification treatment apparatus to which the dust-charged wet desulfurization apparatus of one embodiment of the present invention is applied.

【図5】 本発明の一実施例のダスト荷電湿式脱硫装置
のミストエリミネータ部分の斜視図(ケーシングダクト
などの図示省略)を示す。
FIG. 5 is a perspective view of a mist eliminator portion (a casing duct and the like are omitted) of the dust-charged wet desulfurization apparatus according to an embodiment of the present invention.

【図6】 本発明の一実施例のダスト荷電湿式脱硫装置
のミストエリミネータ部分の水平断面略図を示す。
FIG. 6 is a schematic horizontal cross-sectional view of a mist eliminator portion of a dust-charged wet desulfurization apparatus according to an embodiment of the present invention.

【図7】 従来技術の石炭焚ボイラの排ガスの浄化処理
装置のフローを示す。
FIG. 7 shows a flow of a conventional exhaust gas purification processing apparatus for a coal-fired boiler.

【符号の説明】[Explanation of symbols]

1 ボイラ 2 乾式電気集塵機 3 熱交換器 4 湿式脱硫装置 6 湿式電気集塵機 7 煙突 8 ミストエリミネータ 9 洗浄水溜 10 吸収液スプレ 11 洗浄水スプレ 12 洗浄水スプレ配管 13 送水管 14 吸収液スプレノズル 15 放電電極ワイヤ 16 放電電極配電線 17 ワイヤ支持碍子 18 高電圧発生機 19 接地電極板 20 結合導体 21 接地電極板支持碍
子 22 ミスト捕集板 23 ミスト捕集板支持
碍子 24 管状碍子 25 接地線 26 脱硫吸収塔排ガス入口 27 脱硫吸収塔排ガス
出口 28 ケーシングダクト
1 Boiler 2 Dry Electrostatic Precipitator 3 Heat Exchanger 4 Wet Desulfurization Device 6 Wet Electrostatic Precipitator 7 Chimney 8 Mist Eliminator 9 Cleaning Water Reservoir 10 Absorption Liquid Spray 11 Cleaning Water Spray 12 Cleaning Water Spray Piping 13 Water Pipe 14 Absorption Liquid Spray Nozzle 15 Discharge Electrode Wire 16 Discharge Electrode Distribution Line 17 Wire Support Insulator 18 High Voltage Generator 19 Ground Electrode Plate 20 Coupling Conductor 21 Ground Electrode Plate Support Insulator 22 Mist Collection Plate 23 Mist Collection Plate Support Insulator 24 Tubular Insulator 25 Ground Wire 26 Desulfurization Absorption Tower Exhaust Gas Inlet 27 Desulfurization absorption tower exhaust gas outlet 28 Casing duct

───────────────────────────────────────────────────── フロントページの続き (72)発明者 谷口 憲昭 広島県呉市宝町6番9号 バブコック日立 株式会社呉工場内 ─────────────────────────────────────────────────── ─── Continuation of the front page (72) Inventor Noriaki Taniguchi 6-9 Takaracho, Kure City, Hiroshima Prefecture Babcock Hitachi Kure Factory

Claims (4)

【特許請求の範囲】[Claims] 【請求項1】 処理排ガス出口の排ガスダクトの終端部
にミストエリミネータを有する湿式脱硫吸収塔におい
て、該湿式脱硫吸収塔排ガス出口の排ガスダクト内のミ
ストエリミネータ上流側に放電電極と接地電極とを含む
荷電域を具備し、かつ、ミストエリミネータ内に設けら
れるミスト捕集板と排ガスダクトとの接合部位を電気的
に絶縁し、該ミスト捕集板と該荷電域接地電極とを導体
で結合したことを特徴とするダスト荷電湿式脱硫装置。
1. A wet desulfurization absorber having a mist eliminator at the end of an exhaust gas duct of a treated exhaust gas outlet, including a discharge electrode and a ground electrode upstream of the mist eliminator in the exhaust gas duct of the exhaust gas outlet of the wet desulfurization absorber. Having a charged area and electrically insulating a joint portion between the mist collecting plate provided in the mist eliminator and the exhaust gas duct, and connecting the mist collecting plate and the charged area ground electrode with a conductor. A dust-charged wet desulfurization device characterized by:
【請求項2】 処理排ガス出口の排ガスダクトの終端部
にミストエリミネータを有する湿式脱硫吸収塔におい
て、該湿式脱硫吸収塔排ガス出口の排ガスダクト内のミ
ストエリミネータ上流側に放電電極と接地電極とを含む
荷電域を具備し、かつ、ミストエリミネータ内に設けら
れる並立する多数のミスト捕集板のひとつおきに正の電
荷を印加し、該ミスト捕集板に挟まれる、あるいは前記
ミスト捕集板に隣接するミスト捕集板に負の電荷を印加
することを特徴とするダスト荷電湿式脱硫装置。
2. A wet desulfurization absorber having a mist eliminator at the end of the exhaust gas duct of the treated exhaust gas outlet, including a discharge electrode and a ground electrode upstream of the mist eliminator in the exhaust gas duct of the exhaust gas outlet of the wet desulfurization absorber. A positive charge is applied to every other multiple mist collecting plates that are provided in the mist eliminator and have a charging area, and are sandwiched between the mist collecting plates or adjacent to the mist collecting plate. A dust-charged wet desulfurization device, characterized in that a negative charge is applied to the mist collecting plate.
【請求項3】 放電電極と接地電極とを含む荷電域での
排ガスダクトの断面積よりミスト捕集板が設けられるミ
ストエリミネータ部分の排ガスダクトの断面積を広げる
ことにより、該荷電域での排ガス流速よりも該ミストエ
リミネータ部での排ガス流速を減少させたことを特徴と
する請求項1または請求項2記載のダスト荷電湿式脱硫
装置。
3. Exhaust gas in the charged area by widening the cross-sectional area of the exhaust gas duct in the mist eliminator portion where the mist collecting plate is provided compared to the cross-sectional area of the exhaust gas duct in the charged area including the discharge electrode and the ground electrode. The dust-charged wet desulfurization apparatus according to claim 1 or 2, wherein the exhaust gas flow rate in the mist eliminator section is reduced more than the flow rate.
【請求項4】 接地電極間の導体として、あるいは接地
電極と同符号の接合導体に排ガスダクトを含む構成物導
電部を利用することを特徴とする請求項1ないし3のい
ずれかに記載のダスト荷電湿式脱硫装置。
4. The dust according to claim 1, wherein a constituent conductive portion including an exhaust gas duct is used as a conductor between ground electrodes or as a joint conductor having the same sign as the ground electrode. Charged wet desulfurization equipment.
JP21709695A 1995-08-25 1995-08-25 Dust charged wet desulfurization equipment Expired - Fee Related JP3537553B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP21709695A JP3537553B2 (en) 1995-08-25 1995-08-25 Dust charged wet desulfurization equipment

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP21709695A JP3537553B2 (en) 1995-08-25 1995-08-25 Dust charged wet desulfurization equipment

Publications (2)

Publication Number Publication Date
JPH0957054A true JPH0957054A (en) 1997-03-04
JP3537553B2 JP3537553B2 (en) 2004-06-14

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