JP3896729B2 - Wet electric dust collector - Google Patents

Wet electric dust collector Download PDF

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Publication number
JP3896729B2
JP3896729B2 JP19528899A JP19528899A JP3896729B2 JP 3896729 B2 JP3896729 B2 JP 3896729B2 JP 19528899 A JP19528899 A JP 19528899A JP 19528899 A JP19528899 A JP 19528899A JP 3896729 B2 JP3896729 B2 JP 3896729B2
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Japan
Prior art keywords
needle
electrode
electrostatic precipitator
discharge electrode
dust collecting
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Expired - Fee Related
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JP19528899A
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Japanese (ja)
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JP2001017885A (en
Inventor
美彦 望月
久男 羽田
進一 川畑
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Hitachi Plant Technologies Ltd
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Hitachi Plant Technologies Ltd
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Priority to JP19528899A priority Critical patent/JP3896729B2/en
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Description

【0001】
【発明の属する技術分野】
本発明は、集塵極に噴霧スプレーされた液滴の跳ね返りによって生じるスパーク電圧の低下を防止した湿式電気集塵装置に関する。
【0002】
【従来の技術】
石炭や重油等を燃料とするボイラの排ガス処理システムは、排ガス中の硫黄酸化物を除去するために湿式脱硫装置が設けられ、この後段に煙突からの紫煙防止用に湿式電気集塵装置が配置される。湿式脱硫装置では、排ガス中に循環水等の水を噴霧スプレーし、排ガス温度を飽和温度に低下させ硫黄酸化物を吸収除去している。このため、湿式電気集塵装置には、水や硫酸等のミストを多量に含んだ排ガスが導入される。
放電極と集塵極の間に高電圧を印加すると、排ガス中のミストは放電極からの放電によって放出されたイオンで帯電される。そして電界によって生じるクーロンカで集塵極方向へ移動した後集塵極上に捕集され、スプレー水で洗浄される。従って、ミストの捕集効率は、帯電量が多く印加電圧の高い方が高いため、湿式電気集塵装置はコロナ電流を大きく取れる母材に針を付けた放電極を用いている。
【0003】
【発明が解決しようとする課題】
ところで、コロナ電流は印加電圧を高くできればさらに多くできるが、放電極と集塵極間のスパーク電圧でその上限が決まってしまう。従来の湿式電気集塵装置では、1台の高電圧電源から供給する放電極の母材に付設した針の長さはすべて同じである。従来の湿式電気集塵装置で噴霧スプレーを運転しながら高電圧を印加し、噴霧スプレーの飛散状況及びスパークの発生状況を調べた結果、スパークの発生は主に噴霧スプレーによって集塵極にスプレーされた液滴が集塵極から跳ね返る場所で生じており、また高電圧を印加した状態では眺ね返った液滴が跳ね返り部より下方約100mmの位置までにほとんど集塵極に電気的に捕集されることが確認された。
本発明の目的は、液滴の跳ね返りに起因するスパーク電圧の低下を防止する湿式電気集塵装置を提供することにある。
【0004】
【課題を解決するための手段】
請求項1の発明は、集塵空間中の粒子状物質を、母材に針を付設した構造の放電極に印加した高電圧で電気的に集塵極に捕集させ、上方からの噴霧スプレーによって集塵極の洗浄を行う湿式電気集塵装置において、放電極の母材に付設した針を集塵極に向けるとともに、噴霧スプレーに近い上方に位置する針の長さを短くした構成にある。
また、請求項2の発明は、集塵空間中の粒子状物質を、放電極に印加した高電圧で電気的に集塵極に捕集させ、上方からの噴霧スプレーによって集塵極の洗浄を行う湿式電気集塵装置において、放電極は平板を打ち抜いて形成した母材と針状部を有し、該針状部を集塵極に向けるとともに、噴霧スプレーに近い上方に位置する前記針状部の長さを短くした構成にある。
【0005】
【発明の作用】
請求項1の構成によれば、集塵極にスプレーされた液滴の跳ね返る場所付近に配された放電極の針の長さを短くし、針先端と集塵極の間隔を長くすることにより、液滴の眺ねかえりによって生じるスパーク電圧の低下を防止できる。
請求項2の構成によれば、放電極の母材と針状部が平板により打ち抜きによって作製されているので、製造工程が簡素化されかつ板材の為に加工がし易く、コスト低減が図れる。
本発明によれば、放電極への印加電圧を高くできるので、湿式電気集塵装置のミスト捕集効率を高くできる。
【0006】
【発明の実施の態様】
本発明の実施例について図面を参照しながら説明する。図1は本発明を適用した湿式電気集塵装置の構成図である。
湿式電気集塵装置10は、主として、放電極12、集鹿極14、スプレーノズル16で構成され、これらがハウジング18に収められている。ハウジング18には、処理ガスを導入する入口19と、処理後の清浄ガスを排出する出口20と、および底部分に洗浄時の排水口(図示を省略)が設けられている。湿式電気集塵装置10の内部には入口19からミストを含む処理ガスが矢印30の向きで導入され、ミストを除去した清浄ガスが出口20から排出される。
【0007】
ハウジング18内には、集塵極14と放電極12が所定の間隔で交互に並設されており、両極の間に導入された排ガス中のミストは放電極12からのコロナ放電によって帯電し、クーロン力によって集塵極14に捕集される。放電極12は、図2に示すように母材22に針24を付設した構造になっており、針24は集塵極14に向かって所定間隔にて配されている。図3において、放電極12は、母材22をパイプにて構成し、このパイプの外周に針24の根元を溶接して付設する。針24の長さは、スプレーノズル16からスプレーされた液滴が集塵極14で跳ね返される位置付近までは短くし、それより下方では長くしている。本例ではスプレーノズル16側となる上方に3本の短い針24aを配し、それより下方に長い針24を配した構造になっている。符号23は、パイプ22の上端に溶接等により取り付けれられた蓋である。
【0008】
図4は放電極の他の実施例を示す斜視図である。本実施例は、放電極の母材と集塵極に向けられる針状部を平板から打ち抜いた一体物構造である。放電極12は、所定幅の母材32を対称として複数の針状部34が板面に沿って延設されており、各針状部34は斜めの上方辺と水平な下方辺を持った三角形を成し、母材32の側方に形成されている。スプレーノズル16側に配される上方の複数個の針状部34aは、母材32から三角形の頂点までの長さを短くし、それより下方に配される複数個の針状部34は上方の針状部34aより長くなるよう形成されている。
【0009】
次に本実施例の作用を説明する。
ミストを含む排ガスを湿式電気集塵装置10に導入し、放電極12と集塵極14の間に高電圧を印加する。これによって、ミストは帯電し、クーロン力で集塵極14に捕集される。捕集されたミストは、スプレーノズル16から集塵極14にスプレーされた水で洗い流される。集塵極14にスプレーされた液滴は、図2に示すように集塵極14で跳ね返るが、跳ね返り部付近に配される放電極12からのコロナ放電で、跳ね返り部より下方に100mm以内でほとんどが電気的に捕集される。また、放電極12の針24の長さが短く、針24先端と集塵極14の間隔が長くなっているので、跳ね返りに起因するスパーク電圧が高くなる。従って、湿式電気集塵装置全体の放電極に印加される印加電圧を高くできる。
【0010】
針の長さが短くなった領域では、針先端と集塵極の間隔が長くなるので、コロナ電流が流れにくくなってミストの帯電量が減少し、この領域での集塵性能は低下するが、この領域の高さは集塵極の高さ数千ミリに対し数百ミリ以内であり、全体に占める割合は小さい。一方、湿式電気集塵装置全体の放電極に印加される印加電圧は高くなるので、集塵性能が大幅に向上される。
なお、本実施例は、ガス流が水平の湿式電気集塵装置について説明したが、垂直ガス流の場合にも同様に適用できる。
【0011】
【発明の効果】
本発明によれば、印加電圧を高くできるので、湿式電気集塵装置のミストの捕集効率を高効率に維持できる。
【図面の簡単な説明】
【図1】本発明に係る湿式電気集塵装置を示す構成図である。
【図2】洗浄時のスプレー状況の説明図である。
【図3】放電極の斜視図である。
【図4】放電極の他の実施例の斜視図である。
【符号の説明】
10 湿式電気集塵装置 12 集塵極 14 放電極 16 スプレーノズル 22 母材 24 針
32 母材
34 針状部
[0001]
BACKGROUND OF THE INVENTION
The present invention relates to a wet type electrostatic precipitator that prevents a decrease in spark voltage caused by rebound of droplets sprayed and sprayed on a dust collecting electrode.
[0002]
[Prior art]
The boiler exhaust gas treatment system using coal, heavy oil, etc. as a fuel is equipped with a wet desulfurization device to remove sulfur oxides in the exhaust gas, followed by a wet electrostatic precipitator to prevent purple smoke from the chimney Is done. In the wet desulfurization apparatus, water such as circulating water is spray-sprayed in the exhaust gas, the exhaust gas temperature is lowered to the saturation temperature, and the sulfur oxide is absorbed and removed. For this reason, exhaust gas containing a large amount of mist such as water and sulfuric acid is introduced into the wet electrostatic precipitator.
When a high voltage is applied between the discharge electrode and the dust collecting electrode, the mist in the exhaust gas is charged with ions released by the discharge from the discharge electrode. Then, after moving in the direction of the dust collecting electrode by the coulomb generated by the electric field, it is collected on the dust collecting electrode and washed with spray water. Therefore, since the mist collection efficiency is higher when the charge amount is larger and the applied voltage is higher, the wet electrostatic precipitator uses a discharge electrode in which a needle is attached to a base material capable of obtaining a large corona current.
[0003]
[Problems to be solved by the invention]
By the way, the corona current can be further increased if the applied voltage can be increased, but the upper limit is determined by the spark voltage between the discharge electrode and the dust collecting electrode. In the conventional wet electrostatic precipitator, the lengths of the needles attached to the base material of the discharge electrode supplied from one high voltage power source are all the same. As a result of investigating the spraying state of the spray and the occurrence of sparks while applying a spray while operating the spray with a conventional wet electrostatic precipitator, the occurrence of sparks is mainly sprayed to the dust collecting electrode by the spray. When the high voltage is applied, the liquid droplets that have been viewed are almost collected electrically at the dust collection electrode to a position approximately 100 mm below the rebound part. It was confirmed that
An object of the present invention is to provide a wet type electrostatic precipitator that prevents a decrease in spark voltage caused by droplet rebound.
[0004]
[Means for Solving the Problems]
According to the first aspect of the present invention, the particulate matter in the dust collection space is electrically collected on the dust collection electrode with a high voltage applied to the discharge electrode having a structure in which a needle is attached to the base material, and spray sprayed from above In the wet type electrostatic precipitator that cleans the dust collecting electrode by means of, the needle attached to the base material of the discharge electrode is directed to the dust collecting electrode, and the length of the needle located above the spray spray is shortened .
In the invention of claim 2, particulate matter in the dust collection space is electrically collected on the dust collection electrode with a high voltage applied to the discharge electrode, and the dust collection electrode is cleaned by spraying from above. In the wet type electrostatic precipitator to be performed, the discharge electrode has a base material formed by punching a flat plate and a needle-like part, the needle-like part is directed to the dust collecting electrode, and the needle-like part is located above the spray spray. It is the structure which shortened the length of the part.
[0005]
[Effects of the Invention]
According to the configuration of claim 1, by shortening the length of the needle of the discharge electrode arranged near the place where the droplet sprayed on the dust collecting electrode bounces, and by increasing the distance between the needle tip and the dust collecting electrode. It is possible to prevent a decrease in spark voltage caused by looking back at the droplets.
According to the configuration of the second aspect, since the base material and the needle-like portion of the discharge electrode are produced by punching with a flat plate, the manufacturing process is simplified and the processing for the plate material is easy, and the cost can be reduced.
According to the present invention, since the voltage applied to the discharge electrode can be increased, the mist collection efficiency of the wet electrostatic precipitator can be increased.
[0006]
BEST MODE FOR CARRYING OUT THE INVENTION
Embodiments of the present invention will be described with reference to the drawings. FIG. 1 is a configuration diagram of a wet type electrostatic precipitator to which the present invention is applied.
The wet electrostatic precipitator 10 is mainly composed of a discharge electrode 12, a deer electrode 14, and a spray nozzle 16, which are housed in a housing 18. The housing 18 is provided with an inlet 19 for introducing the processing gas, an outlet 20 for discharging the treated clean gas, and a drain (not shown) for cleaning at the bottom. A processing gas containing mist is introduced into the wet electrostatic precipitator 10 from the inlet 19 in the direction of the arrow 30, and the clean gas from which the mist has been removed is discharged from the outlet 20.
[0007]
In the housing 18, dust collecting electrodes 14 and discharge electrodes 12 are alternately arranged at predetermined intervals, and mist in the exhaust gas introduced between both electrodes is charged by corona discharge from the discharge electrodes 12. It is collected by the dust collecting electrode 14 by Coulomb force. As shown in FIG. 2, the discharge electrode 12 has a structure in which a needle 24 is attached to a base material 22, and the needle 24 is arranged at a predetermined interval toward the dust collection electrode 14. In FIG. 3, the discharge electrode 12 is formed by forming a base material 22 with a pipe and welding the root of a needle 24 to the outer periphery of the pipe. The length of the needle 24 is shortened to the vicinity of the position where the droplet sprayed from the spray nozzle 16 rebounds at the dust collection electrode 14, and is made longer below that position. In this example, three short needles 24a are arranged above the spray nozzle 16 side, and long needles 24 are arranged below it. Reference numeral 23 denotes a lid attached to the upper end of the pipe 22 by welding or the like.
[0008]
FIG. 4 is a perspective view showing another embodiment of the discharge electrode. In the present embodiment, the base material of the discharge electrode and the needle-like portion directed to the dust collecting electrode are punched out from a flat plate. The discharge electrode 12 has a plurality of needle-like portions 34 extending along the plate surface with a base material 32 having a predetermined width symmetrical, and each needle-like portion 34 has an oblique upper side and a horizontal lower side. It forms a triangle and is formed on the side of the base material 32. The plurality of upper needle-like parts 34a arranged on the spray nozzle 16 side shorten the length from the base material 32 to the apex of the triangle, and the plurality of needle-like parts 34 arranged below the upper part are upper It is formed to be longer than the needle-like portion 34a.
[0009]
Next, the operation of this embodiment will be described.
Exhaust gas containing mist is introduced into the wet electrostatic precipitator 10 and a high voltage is applied between the discharge electrode 12 and the dust collecting electrode 14. As a result, the mist is charged and collected on the dust collecting electrode 14 by Coulomb force. The collected mist is washed away with water sprayed from the spray nozzle 16 to the dust collecting electrode 14. The droplet sprayed on the dust collecting electrode 14 bounces off at the dust collecting electrode 14 as shown in FIG. 2, but it is within 100 mm below the bounce portion due to corona discharge from the discharge electrode 12 arranged in the vicinity of the bounce portion. Most are collected electrically. Further, since the length of the needle 24 of the discharge electrode 12 is short and the distance between the tip of the needle 24 and the dust collecting electrode 14 is long, the spark voltage due to the rebound is increased. Therefore, the applied voltage applied to the discharge electrode of the entire wet electrostatic precipitator can be increased.
[0010]
In the area where the length of the needle is shortened, the distance between the needle tip and the dust collecting electrode becomes long, so that the corona current is difficult to flow and the amount of mist charge is reduced, and the dust collecting performance in this area is reduced. The height of this region is within several hundred millimeters compared to several thousand millimeters of the height of the dust collecting electrode, and the ratio of the total area is small. On the other hand, since the applied voltage applied to the discharge electrode of the entire wet electrostatic precipitator increases, the dust collection performance is greatly improved.
In addition, although the present Example demonstrated the wet-type electrostatic precipitator with a horizontal gas flow, it is applicable similarly to the case of a vertical gas flow.
[0011]
【The invention's effect】
According to the present invention, since the applied voltage can be increased, the mist collection efficiency of the wet electrostatic precipitator can be maintained at high efficiency.
[Brief description of the drawings]
FIG. 1 is a configuration diagram illustrating a wet electrostatic precipitator according to the present invention.
FIG. 2 is an explanatory diagram of a spray situation during cleaning.
FIG. 3 is a perspective view of a discharge electrode.
FIG. 4 is a perspective view of another embodiment of a discharge electrode.
[Explanation of symbols]
DESCRIPTION OF SYMBOLS 10 Wet electrostatic precipitator 12 Dust collection electrode 14 Discharge electrode 16 Spray nozzle 22 Base material 24 Needle 32 Base material 34 Needle-shaped part

Claims (2)

集塵空間中の粒子状物質を、母材に針を付設した構造の放電極に印加した高電圧で電気的に集塵極に捕集させ、上方からの噴霧スプレーによって集塵極の洗浄を行う湿式電気集塵装置において、
前記放電極の母材に付設した針を集塵極に向けるとともに、前記噴霧スプレーに近い上方に位置する前記針の長さを短くしたことを特徴とする湿式電気集塵装置。
Particulate matter in the dust collection space is electrically collected on the dust collection electrode with a high voltage applied to the discharge electrode with a needle attached to the base material, and the dust collection electrode is cleaned by spraying from above. In the wet electrostatic precipitator to perform,
A wet electrostatic precipitator characterized in that a needle attached to a base material of the discharge electrode is directed to a dust collecting electrode, and the length of the needle located above the spray is shortened.
集塵空間中の粒子状物質を、放電極に印加した高電圧で電気的に集塵極に捕集させ、上方からの噴霧スプレーによって集塵極の洗浄を行う湿式電気集塵装置において、
前記放電極は平板を打ち抜いて形成した母材と針状部を有し、該針状部を集塵極に向けるとともに、前記噴霧スプレーに近い上方に位置する前記針状部の長さを短くしたことを特徴とする湿式電気集塵装置。
In a wet type electrostatic precipitator that collects particulate matter in the dust collection space electrically with a high voltage applied to the discharge electrode and collects the dust collection electrode by spraying from above.
The discharge electrode has a base material formed by punching a flat plate and a needle-like portion, and directs the needle-like portion toward the dust collecting electrode and shortens the length of the needle-like portion located above the spray spray. Wet electrostatic precipitator characterized by the above.
JP19528899A 1999-07-09 1999-07-09 Wet electric dust collector Expired - Fee Related JP3896729B2 (en)

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RU2448778C1 (en) * 2010-08-05 2012-04-27 Закрытое акционерное общество "Кондор-Эко" Electric filter with self-centering corona-forming elements
WO2015068209A1 (en) * 2013-11-05 2015-05-14 三菱重工メカトロシステムズ株式会社 Dust collection device and dust collection method
KR101852163B1 (en) 2017-03-15 2018-06-04 동원중공업(주) An apparatus combined electrostatic spraying with electrostatic precipitator for removing fine particulate matter
KR101985693B1 (en) * 2017-09-29 2019-06-04 한국에너지기술연구원 Apparatus for Simultaneous Removal of Tar and Dust with Gas Engine Application for Distributed Power Generation
KR101953743B1 (en) 2017-11-16 2019-03-04 한국에너지기술연구원 Apparatus for Removing Fine Particles Agglomeration with Highly-Charged Mist Spraying
KR101882283B1 (en) 2017-11-28 2018-07-26 동원중공업(주) A Cyclone Air Purifier having Electro Spraying
US10888813B2 (en) 2018-05-07 2021-01-12 Korea Institute Of Energy Research Wet type dust collector using electrospray and vortex

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