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JPH01164460A - Dust collector with electrically charged particle packing layer - Google Patents

Dust collector with electrically charged particle packing layer

Info

Publication number
JPH01164460A
JPH01164460A JP62321326A JP32132687A JPH01164460A JP H01164460 A JPH01164460 A JP H01164460A JP 62321326 A JP62321326 A JP 62321326A JP 32132687 A JP32132687 A JP 32132687A JP H01164460 A JPH01164460 A JP H01164460A
Authority
JP
Japan
Prior art keywords
dust
gas
particles
charged particle
packing material
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
JP62321326A
Other languages
Japanese (ja)
Inventor
Hisao Makino
尚夫 牧野
Tsutae Nagayama
永山 伝
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.)
Central Research Institute of Electric Power Industry
Original Assignee
Central Research Institute of Electric Power Industry
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 Central Research Institute of Electric Power Industry filed Critical Central Research Institute of Electric Power Industry
Priority to JP62321326A priority Critical patent/JPH01164460A/en
Publication of JPH01164460A publication Critical patent/JPH01164460A/en
Pending legal-status Critical Current

Links

Classifications

    • BPERFORMING OPERATIONS; TRANSPORTING
    • B03SEPARATION OF SOLID MATERIALS USING LIQUIDS OR USING PNEUMATIC TABLES OR JIGS; MAGNETIC OR ELECTROSTATIC SEPARATION OF SOLID MATERIALS FROM SOLID MATERIALS OR FLUIDS; SEPARATION BY HIGH-VOLTAGE ELECTRIC FIELDS
    • B03CMAGNETIC OR ELECTROSTATIC SEPARATION OF SOLID MATERIALS FROM SOLID MATERIALS OR FLUIDS; SEPARATION BY HIGH-VOLTAGE ELECTRIC FIELDS
    • B03C3/00Separating dispersed particles from gases or vapour, e.g. air, by electrostatic effect
    • B03C3/02Plant or installations having external electricity supply
    • B03C3/04Plant or installations having external electricity supply dry type
    • B03C3/14Plant or installations having external electricity supply dry type characterised by the additional use of mechanical effects, e.g. gravity
    • B03C3/145Inertia

Landscapes

  • Electrostatic Separation (AREA)

Abstract

PURPOSE:To stably collect dust even small particles of soot with low electric resistance by flowing the gas contg. dust from lower part to upper part through the electrically charged particle packing layer dust collector in which newly charged particles are supplied from the upper part and polluted particles are discharged from the lower part. CONSTITUTION:The packing material 2 is supplied into a dust collecting vessel 1 from a supply system 3 and a discharge electrode 8 is charged with high voltage to impress voltage to the packing material 2 existing between the discharge electrode 8 and the confronting electrode, that is, the dust collecting vessel 1. On the other hand, the gas contg. dust is flowed from a dust contg. gas introducing opening 5 through the space between the electrodes 1, 8 and, at the same time, new packing material 2 is supplied from the upper part to collect dust. The polluted packing material 2 is discharged through a discharge system 4 and the gas deprived of dust is discharged from a gas discharge opening 6 in the upper part. As a result, the gas of low dust concn. is deprived of dust in the upper part and the gas of high dust concn. is deprived of dust in the lower part with the result that the utilizing efficiency of packing material and the dust collecting efficiency are raised.

Description

【発明の詳細な説明】 (産業上の利用分野) 本発明は電気集塵器に関する。更に詳述すると、本発明
は荷電粒子を放電極間に充填し、静電集塵と濾過集塵と
を複合化した荷電粒子充填層集塵器に関する。
DETAILED DESCRIPTION OF THE INVENTION (Field of Industrial Application) The present invention relates to an electrostatic precipitator. More specifically, the present invention relates to a charged particle packed bed dust collector in which charged particles are filled between discharge electrodes to combine electrostatic dust collection and filtration dust collection.

(従来の技術) 従来の荷電粒子充填層集塵器としては、第7図に示され
るように、荷電粒子103を充填した集塵容器101に
該容器101を横切るように含塵ガスを導入して集塵す
る直交流型がある。この集塵器は、集塵容器101を充
填する荷電粒子103の移動方向と直交する方向に含塵
ガスを流して集塵するもので、集塵容器の上から下まで
放電電極102を設置すると共にこのj&Ijl容器1
01の上から下に向けて荷電粒子103を移動さぜるよ
うにしている。尚、符号104は電源である。
(Prior Art) As shown in FIG. 7, in a conventional charged particle packed bed dust collector, a dust-containing gas is introduced into a dust collection container 101 filled with charged particles 103 so as to cross the container 101. There is a cross-flow type that collects dust. This dust collector collects dust by flowing a dust-containing gas in a direction perpendicular to the moving direction of charged particles 103 filling a dust collection container 101, and discharge electrodes 102 are installed from the top to the bottom of the dust collection container. Along with this j & Ijl container 1
The charged particles 103 are moved from above to below 01. Note that the reference numeral 104 is a power source.

(発明が解決しようとする問題点) しかしながら、この直交型荷電粒子充填層集塵器による
と、低電気抵抗のばいじん(重油圧や石炭ガス化チャー
等)を捕集する場合、充填材たる荷電粒子103の表面
に171着したばいじんを漏洩電流が流れるようになり
、印加電圧が低下し、電界による集塵効果がなくなって
しまう。これをI!Jjぐためには、移動速症を極端に
速くする必要かあるが、ガス流速が上昇するため一度捕
集したばいじんが再飛散しく流体力学的再飛散現象)、
集塵効率が極端に低下する欠点がある。また、排出され
る荷電粒子即ち充填材103も、ガス流入口側は大量の
ばいじんを捕集しているのに対し、ガス排出側はほとん
どばいじんを捕集しておらず、無駄になる充填材が生じ
る。斯様に従来の荷電粒子充填層集塵器は、電気抵抗が
低いばいじんに対しての使用に適していない欠点がある
(Problem to be solved by the invention) However, according to this orthogonal charged particle packed bed precipitator, when collecting low electrical resistance dust (such as heavy hydraulic pressure or coal gasification char), it is difficult to A leakage current begins to flow through the dust 171 deposited on the surface of the particles 103, the applied voltage decreases, and the dust collection effect by the electric field disappears. This is I! In order to achieve this, it is necessary to make the movement speed extremely fast, but as the gas flow rate increases, the collected soot and dust will be re-entrained (hydrodynamic re-entrainment phenomenon).
The drawback is that the dust collection efficiency is extremely low. Furthermore, regarding the charged particles that are discharged, that is, the filler 103, while a large amount of soot and dust is collected on the gas inlet side, almost no soot and dust is collected on the gas discharge side, and the filler is wasted. occurs. As such, conventional charged particle packed bed precipitators have the disadvantage that they are not suitable for use with soot and dust having low electrical resistance.

本発明は低電気抵抗の粒子状物質を高い集塵効率で連続
的に安定した状態で捕集することが可能な荷電粒子充填
層集塵器を提供することを目的とする。
SUMMARY OF THE INVENTION An object of the present invention is to provide a charged particle packed bed dust collector that can continuously and stably collect particulate matter having low electrical resistance with high dust collection efficiency.

(問題点を解決するための手段) かかる目的を達成するため、本発明の荷電粒子充填層集
塵器は、集塵容器内の放電極とその対向電極間に誘電率
の高い絶縁性の粒子を充填し、前記電極間に下部より含
塵気体を流入させると共に上部から新たな充填粒子を供
給して集塵し、下部より、集塵により汚染した充填粒子
を排出する一方、L部より除塵後の気体を排出するよう
にしている。
(Means for Solving the Problems) In order to achieve the above object, the charged particle packed bed precipitator of the present invention includes insulating particles having a high dielectric constant between the discharge electrode and its counter electrode in the dust collection container. A dust-containing gas is introduced between the electrodes from the lower part, and new filled particles are supplied from the upper part to collect the dust. The filled particles contaminated by the dust collection are discharged from the lower part, while the dust is removed from the L part. The remaining gas is expelled.

また、本発明の荷電粒子充填層集塵器は、放電極の長さ
を短くし、充填層下部のばいじん捕集後の汚染充填粒子
には電圧を印加しない構造としたことを特徴とする。
Further, the charged particle packed bed precipitator of the present invention is characterized by having a structure in which the length of the discharge electrode is shortened and no voltage is applied to the contaminated packed particles after collecting soot and dust at the bottom of the packed bed.

(作用) したがって、上部の新たに供給された充填材は、既に下
部にて集塵された後の粉塵負荷の低いガスを集塵し、ま
た下部の既に長時間集塵して汚れた充填材は集塵器入口
の粉塵負荷の高いカスを集塵する。このため、充填層内
の粉塵負荷は、第2図(B)のように極端に下部が高く
なり、低電気抵抗ばいじんの充填材付着による漏洩電流
増大域が第2図(A)に示す従来の集塵器よりも小さく
なる。
(Function) Therefore, the newly supplied filling material in the upper part collects the gas with a low dust load that has already been collected in the lower part, and also the filling material in the lower part which has already been collected for a long time and is dirty. Collects scum with a high dust load at the dust collector inlet. For this reason, the dust load in the packed bed is extremely high at the bottom as shown in Figure 2 (B), and the leakage current increase area due to the adhesion of low electrical resistance dust to the filler is as shown in Figure 2 (A). smaller than the standard dust collector.

また、短電極とする場合、前置集塵としての粒子充填層
集塵器と、精密集塵としての荷電粒子充填層集塵器とを
一体化した集塵器となる。
In addition, when a short electrode is used, the precipitator becomes a precipitator that integrates a particle packed bed precipitator as a pre-dust collector and a charged particle packed bed precipitator as a precision dust collector.

(実施例) 以下、本発明の構成を図面に示す実施例に基づいて詳細
に説明する。
(Example) Hereinafter, the configuration of the present invention will be described in detail based on an example shown in the drawings.

第1図に本発明の荷電粒子充填層集塵器の一実施例を示
す。尚、本実施例では、集塵効果等の基礎実験を実施す
るため含塵ガスを作り出す装置や測定器具を集塵容器1
の入口及び出口側に接続しているが、これら機器が本発
明の必要不可欠なものでないことは言うまでもない。
FIG. 1 shows an embodiment of the charged particle packed bed dust collector of the present invention. In this example, in order to conduct basic experiments such as the dust collection effect, a device for producing dust-containing gas and a measuring instrument were installed in the dust collection container 1.
However, it goes without saying that these devices are not essential to the present invention.

この集塵器は、荷電粒子2を充填し高電圧を荷電してい
る筒状の集塵容器1と、該集塵容器1の上流側から充填
材たる荷電粒子(以下充填材とも言う)2を供給する充
填材供給系3と、前記集塵器本体1の下流側において充
填材2を排出する充填材排出系4と、集塵容器1内に設
置される放電極8及びその付帯設備とから成り、充填材
2を上方から流下させて下方から排出する一方、下方か
ら含塵ガスを導入して上流側から取出すようにし、充填
材2と含塵ガスとを自流接触させるように設けられてい
る。
This dust collector includes a cylindrical dust collection container 1 filled with charged particles 2 and charged with a high voltage, and charged particles (hereinafter also referred to as filler) 2 as a filler from the upstream side of the dust collection container 1. a filler supply system 3 that supplies the filler 2, a filler discharge system 4 that discharges the filler 2 on the downstream side of the dust collector main body 1, a discharge electrode 8 installed in the dust collection container 1, and its ancillary equipment. The filling material 2 is made to flow down from above and discharged from below, while the dust-containing gas is introduced from below and taken out from the upstream side, so that the filling material 2 and the dust-containing gas are brought into self-flow contact. ing.

集塵容器1は接地され、その中央の放電l#18の対向
電極を構成するように設けられている。したがって、こ
の集塵容器1内を流下する充填材2は放電極とその対向
電極との間を充填しつつ移動することとなる。また、こ
の集塵容器1の含塵カス流入口6は下部に、ガス排出口
5は上部に設けら。
The dust collecting container 1 is grounded and is provided so as to constitute a counter electrode for the discharge l#18 in the center thereof. Therefore, the filling material 2 flowing down inside the dust collecting container 1 moves while filling the gap between the discharge electrode and its counter electrode. Further, the dust-containing scum inlet 6 of this dust collecting container 1 is provided at the lower part, and the gas outlet 5 is provided at the upper part.

れ、充填材の移動方向とは逆方向に含塵ガスを移動させ
て充填材2の全てと向流接触させるように設けられてい
る。また、この集塵容器1の上部及び下部には、充填材
の供給及び排出を図ると共にその量をコントロールする
ための手段例えばロールフィーダ9,10が設けられて
いる。したがって、充填材供給系3のフィーダつと排出
系4のフィーダ10を夫々制御することによって充填材
2の移動速度を調整することができる。更に、上述の集
塵器の含塵ガス導入口5には、人工的に含塵ガスを作り
出し供給するため、除湿器51、絶対フィルタ52、チ
ャー供給器53、エゼクタ54、ばい塵濃度測定器55
及び温度測定器56が接続されている。また、ガス排出
口6には温度測定器61、煤塵濃度測定器62、絶対フ
ィルタ63、吸引ファン64及びガスメータ65が順次
接続されている。
The dust-containing gas is moved in a direction opposite to the moving direction of the filler 2, and is provided so as to come into countercurrent contact with all of the filler 2. Moreover, means for supplying and discharging the filler and controlling the amount thereof, such as roll feeders 9 and 10, are provided at the upper and lower parts of the dust collecting container 1. Therefore, the moving speed of the filler 2 can be adjusted by controlling the feeder of the filler supply system 3 and the feeder 10 of the discharge system 4, respectively. Further, the dust-containing gas inlet 5 of the above-mentioned dust collector is equipped with a dehumidifier 51, an absolute filter 52, a char supply device 53, an ejector 54, and a dust concentration measuring device in order to artificially generate and supply dust-containing gas. 55
and a temperature measuring device 56 are connected. Further, a temperature measuring device 61, a soot/dust concentration measuring device 62, an absolute filter 63, a suction fan 64, and a gas meter 65 are connected to the gas outlet 6 in this order.

また、充填材となる荷電粒子2としては、誘電率の高い
絶縁性の粒子、例えばムライト粒子や焦合、10Ill
IIφのムライト粒子が使用されている。
Further, as the charged particles 2 serving as the filler, insulating particles with a high dielectric constant, such as mullite particles, focused particles, 10Ill
IIφ mullite particles are used.

尚、図中符号7は高電圧荷電源、8は放電極である。本
実施例の場合、放電極8は集塵容器1の最下部まで達し
ないような短電極とし、充填層の下部のばい塵捕集後の
汚染した充填材2には電圧を印加しない構造としている
。即ち、第2図(B)に示す漏洩電流増大域に荷電をし
ないような放電極長であれば良い。このため、漏洩電流
増大域が従来の集塵器よりも小さくかつ下層にある本発
明装置の場合、短電極とは言っても充填層のほとんどの
部分に電圧を印加することが可能となるし、処理ガス全
量が荷電充填層部を通過するために短電極としても高集
塵効率が期待できる。
In the figure, numeral 7 is a high-voltage charge source, and 8 is a discharge electrode. In the case of this embodiment, the discharge electrode 8 is a short electrode that does not reach the lowest part of the dust collection container 1, and the structure is such that no voltage is applied to the contaminated filling material 2 after dust collection at the bottom of the filling bed. There is. That is, the discharge electrode length may be such that it does not charge the leakage current increasing region shown in FIG. 2(B). For this reason, in the case of the device of the present invention, where the leakage current increase area is smaller than that of conventional precipitators and is located in the lower layer, it is possible to apply voltage to most parts of the packed bed, even though it is a short electrode. Since the entire amount of processing gas passes through the charged packed layer, high dust collection efficiency can be expected even with a short electrode.

以上のように構成された荷電粒子充填層集塵器によると
、次のようにして集塵は行なわれる。
According to the charged particle packed bed precipitator configured as described above, dust collection is performed in the following manner.

まず、集塵容器1内に充填材2を供給系3から供給して
充填すると共に放電極8に高電圧をかけて放電極8とそ
の対向電極たる集塵容器1との間の充填材2に電圧を印
加する。一方、集塵容器1の下部の含塵ガス導入口5か
ら電極1,8間に含塵ガスを流入させると共に上部から
新たな充填粒子2を供給してS塵する。そして汚染した
充填粒子2を下部の排出系4から排出する一方、上部の
ガス排出口6より除塵後の気体を排出する。
First, the filling material 2 is supplied from the supply system 3 into the dust collecting container 1, and a high voltage is applied to the discharge electrode 8 to place the filling material 2 between the discharge electrode 8 and the dust collecting container 1, which is the opposite electrode. Apply voltage to. On the other hand, a dust-containing gas is introduced between the electrodes 1 and 8 from a dust-containing gas inlet 5 at the bottom of the dust collection container 1, and new filling particles 2 are supplied from the top to generate S dust. Then, while the contaminated packed particles 2 are discharged from the lower discharge system 4, the gas after dust removal is discharged from the upper gas discharge port 6.

このとき、充填材2の移動速度は処理ガス中のばいじん
負荷によって決定され、高ばいじん濃度あるいは高流速
などによってばいじん負荷が高い場合には移動速度を増
加し、逆にばいじん負荷が低い場合には移動速度を低下
することによって安定でかつ高集塵効率の運転が行える
。例えば、入口ばいじん濃度3Q7m3、集塵流速21
cm/SeCで集塵する場合1.33m/hr以上の移
動速度とすることが好ましい。この場合の印加電圧の経
時変化を示した第3図及び放電電流の経時変化を示した
第4図に明らかように、固定層運転即ち荷電粒子2を移
動させない場合、約30秒経過後に放電電流が増大を始
め、1分後には印加電圧が低下し始める。そして、約2
分後には、漏洩電流の極端な増大により電圧印加不能に
至る。しかし、本発明の自流移動層型として移動速度を
増加させると印加可能時間は延長され、移動速度1.3
3m/llr以上では連続運転が可能となり、常時安定
した荷電を行うことができる。更に、同様の実験を、チ
ャー濃度、濾過速度を変化させて行った時の連続運転可
能となる充填材移動速度の測定結果第5図に示すと、そ
れぞれの実験条件より高い充填材移動速度にすれば常に
連続運転が可能となることが理解できる。
At this time, the moving speed of the filler 2 is determined by the soot and dust load in the process gas, and when the soot and dust load is high due to high soot and dust concentration or high flow rate, the movement speed is increased, and conversely, when the soot and dust load is low, the movement speed is increased. By lowering the moving speed, stable operation with high dust collection efficiency can be achieved. For example, the inlet dust concentration is 3Q7m3, the dust collection flow rate is 21
When collecting dust at cm/SeC, the moving speed is preferably 1.33 m/hr or more. As is clear from Figure 3, which shows the time-dependent change in the applied voltage in this case, and Figure 4, which shows the time-dependent change in the discharge current, in fixed bed operation, that is, when the charged particles 2 are not moved, the discharge current changes after approximately 30 seconds. begins to increase, and after 1 minute, the applied voltage begins to decrease. And about 2
After a few minutes, voltage application becomes impossible due to an extreme increase in leakage current. However, when the moving speed of the self-flowing moving bed type of the present invention is increased, the applicable time is extended, and the moving speed is 1.3.
Continuous operation is possible at 3 m/llr or more, and stable charging can be performed at all times. Furthermore, Figure 5 shows the measurement results of the filler movement speed that enabled continuous operation when a similar experiment was conducted while changing the char concentration and filtration rate. This will help you understand that continuous operation is always possible.

(発明の効果) 以上の説明より明らかなように、本発明の荷電粒子充填
層集塵器は、集塵容器内の放電極とその対向電極間に誘
電率の高い絶縁性の粒子を充填し、前記電極間に下部よ
り含塵気体を流入させると共に上部から新たな充填粒子
を供給して#?、塵し、下部より、集塵により汚染した
充填粒子を排出する一方、上部より除塵後の気体を排出
するようにしているので、上部の新たに供給された充填
材は、既に下部にて集塵された後の粉塵負荷の低いガス
を集塵し、また下部の既に長時間集塵して汚れた充填材
は集塵器入口の粉塵負荷の高いガスを集塵する。このた
め、充填層内の粉塵負荷は、第2図(B)のように極端
に下部か高くなり、低電気抵抗ばいじんの充填材付着に
よる漏洩電流増大域か第2図<A)に示す従来の集塵器
よりも小さくなる。
(Effects of the Invention) As is clear from the above explanation, the charged particle packed bed precipitator of the present invention fills insulating particles with a high dielectric constant between the discharge electrode and its counter electrode in the dust collection container. , a dust-containing gas is introduced from the bottom between the electrodes, and new filling particles are supplied from the top. The packed particles contaminated by dust collection are discharged from the lower part, while the gas after dust removal is discharged from the upper part, so the newly supplied filling material in the upper part has already been collected in the lower part. The gas with a low dust load after being dusted is collected, and the filling material at the bottom, which has already been contaminated for a long time, collects the gas with a high dust load at the entrance of the dust collector. For this reason, the dust load in the packed bed is extremely high at the bottom as shown in Figure 2 (B), and it is likely that the leakage current increases due to the adhesion of low electrical resistance dust to the filler, as shown in Figure 2 <A). smaller than the standard dust collector.

したかって、本発明によると、集塵性能の高い荷電粒子
充填層集塵器を低電気抵抗のばいじんに対しても使用で
きるようになるため、導電性のばいじんから電気抵抗の
高いばいじんまで幅広い性状の捕集対象に対して高集塵
効率で、圧力損失が低くかつ充填材の効率の良い活用が
行え実用上の効果は大きい。例えば、本発明の荷電粒子
充填集塵器の集塵性能を無荷電の状@(濾過集電)と比
軸した第6図の実験結果によると、品も集塵し難い粒径
的1μm程度の粒子に対して無荷電状態では集塵率50
%程度にしかならないのに対して、本方式は98%程度
にまでなり、出口濃度としては約20分の1まで低減で
きる2、tな、従来の荷電粒子充填層集塵器に比べて荷
電粒子表面での漏洩電流の流れが少ないので、移動速度
が小さくて済み、再飛散を防止できる。
Therefore, according to the present invention, a charged particle packed bed precipitator with high dust collection performance can be used for dust with low electrical resistance, so it can handle dust with a wide range of properties from conductive dust to dust with high electrical resistance. It has high dust collection efficiency for the objects to be collected, low pressure loss, and efficient use of the filler material, which has great practical effects. For example, according to the experimental results shown in Figure 6, which compares the dust collection performance of the charged particle-filled dust collector of the present invention with that of the uncharged state (filtration current collection), it is found that the particle size is about 1 μm, which makes it difficult to collect dust. The dust collection rate is 50 in the uncharged state for particles of
Compared to the conventional charged particle packed bed precipitator, this method can reduce the charged particle concentration to about 98%, and the outlet concentration can be reduced to about one-twentieth. Since the flow of leakage current on the particle surface is small, the movement speed is small and re-scattering can be prevented.

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

第1図は本発明の荷電粒子充填層集塵器の一実施例を基
礎実験装置として組込んだ状態で示す原理図、第2図(
A>、(B)は従来の荷電粒子充填層集塵器と本発明の
荷電粒子充填層集塵器の層内のダスト負荷と電気抵抗分
布との関係を示すグラフ、第3図〜第6図は本発明の実
験結果を示すグラフで、第3図は移動速度をパラメータ
にした印加電圧の経時変化、第4図は移動速度をパラメ
ータにした放電電流の経時変化、第5図はチャー濃度を
パラメータにして濾過速度と連続運転が可能となる充填
材移動速度との関係、第6図は本発明方式集塵器と粒子
充填式集塵器との集塵性能を捕集対象の粒径側に比較し
たものである。第7図は従来の荷電粒子充填集塵器の一
例を示す構造概略図である。 1・・・集塵容器(対向電極)、 2・・・充填材(荷電粒子)、 3・・・充填材供給系、4・・・充填材排出系、5・・
・含塵ガス導入口、6・・・ガス排出口、7・・・高電
圧荷電源、8・・・電極、9.10・・・荷電粒子の移
動速度をコントロールする手段(フィーダ)。 特許出願人  財団法人 電力中央研究所第2図 (A) (B) 第 7 図
Figure 1 is a principle diagram showing one embodiment of the charged particle packed bed precipitator of the present invention installed as a basic experimental device, and Figure 2 (
A>, (B) are graphs showing the relationship between the dust load and electrical resistance distribution in the layers of the conventional charged particle packed bed precipitator and the charged particle packed bed precipitator of the present invention, FIGS. 3 to 6 The figure is a graph showing the experimental results of the present invention. Figure 3 is the change in applied voltage over time with the moving speed as a parameter, Figure 4 is the change in discharge current over time with the moving speed as a parameter, and Figure 5 is the char concentration. Figure 6 shows the relationship between the filtration speed and the moving speed of the filler that enables continuous operation using the parameter . This is compared to the side. FIG. 7 is a schematic structural diagram showing an example of a conventional charged particle-filled dust collector. 1... Dust collection container (counter electrode), 2... Filler (charged particles), 3... Filler supply system, 4... Filler discharge system, 5...
- Dust-containing gas inlet, 6... Gas outlet, 7... High voltage charging power source, 8... Electrode, 9.10... Means for controlling the moving speed of charged particles (feeder). Patent applicant Central Research Institute of Electric Power Industry Figure 2 (A) (B) Figure 7

Claims (2)

【特許請求の範囲】[Claims] (1)集塵容器内の放電極とその対向電極間に誘電率の
高い絶縁性の粒子を充填し、前記電極間に下部より含塵
気体を流入させると共に上部から新たな充填粒子を供給
して集塵し、下部より汚染した充填粒子を排出する一方
、上部より除塵後の気体を排出することを特徴とする荷
電粒子充填層集塵器。
(1) Insulating particles with a high dielectric constant are filled between a discharge electrode and its counter electrode in a dust collection container, and a dust-containing gas is introduced from the bottom between the electrodes, and new filling particles are supplied from the top. A charged particle packed bed dust collector is characterized in that the charged particle packed bed dust collector collects dust and discharges the contaminated packed particles from the lower part, while the gas after dust removal is discharged from the upper part.
(2)前記放電極の長さを短くし、充填層下部のばいじ
ん捕集後の汚染充填粒子には電圧を印加しない構造とし
たことを特徴とする特許請求の範囲第1項に記載の荷電
粒子充填層集塵器。
(2) The charged electric charge according to claim 1, characterized in that the length of the discharge electrode is shortened, and a structure is adopted in which no voltage is applied to the contaminated packed particles after collecting soot and dust at the bottom of the packed bed. Particle packed bed dust collector.
JP62321326A 1987-12-21 1987-12-21 Dust collector with electrically charged particle packing layer Pending JPH01164460A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP62321326A JPH01164460A (en) 1987-12-21 1987-12-21 Dust collector with electrically charged particle packing layer

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP62321326A JPH01164460A (en) 1987-12-21 1987-12-21 Dust collector with electrically charged particle packing layer

Publications (1)

Publication Number Publication Date
JPH01164460A true JPH01164460A (en) 1989-06-28

Family

ID=18131343

Family Applications (1)

Application Number Title Priority Date Filing Date
JP62321326A Pending JPH01164460A (en) 1987-12-21 1987-12-21 Dust collector with electrically charged particle packing layer

Country Status (1)

Country Link
JP (1) JPH01164460A (en)

Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS5586512A (en) * 1978-12-25 1980-06-30 Chiyoda Chem Eng & Constr Co Ltd Electrostatic filter
JPS56141854A (en) * 1980-04-04 1981-11-05 Chiyoda Chem Eng & Constr Co Ltd Electrostatic filter
JPS57130560A (en) * 1980-12-18 1982-08-13 Gen Electric Granule bed filter for high-temperature powder and granule removal electrostatically reinforced and powder and granule removing method

Patent Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS5586512A (en) * 1978-12-25 1980-06-30 Chiyoda Chem Eng & Constr Co Ltd Electrostatic filter
JPS56141854A (en) * 1980-04-04 1981-11-05 Chiyoda Chem Eng & Constr Co Ltd Electrostatic filter
JPS57130560A (en) * 1980-12-18 1982-08-13 Gen Electric Granule bed filter for high-temperature powder and granule removal electrostatically reinforced and powder and granule removing method

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