JPH01299647A - Multiple electric field-type electrostatic fluocculator - Google Patents
Multiple electric field-type electrostatic fluocculatorInfo
- Publication number
- JPH01299647A JPH01299647A JP63128243A JP12824388A JPH01299647A JP H01299647 A JPH01299647 A JP H01299647A JP 63128243 A JP63128243 A JP 63128243A JP 12824388 A JP12824388 A JP 12824388A JP H01299647 A JPH01299647 A JP H01299647A
- Authority
- JP
- Japan
- Prior art keywords
- electric field
- electric
- particles
- dust
- field
- 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
Links
- 230000005684 electric field Effects 0.000 claims abstract description 52
- 239000000428 dust Substances 0.000 claims abstract description 39
- 239000012530 fluid Substances 0.000 claims abstract description 18
- 238000009833 condensation Methods 0.000 claims description 5
- 230000005494 condensation Effects 0.000 claims description 5
- 230000005405 multipole Effects 0.000 claims description 4
- 239000002245 particle Substances 0.000 abstract description 44
- 239000010881 fly ash Substances 0.000 abstract description 12
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 abstract description 9
- 229910052799 carbon Inorganic materials 0.000 abstract description 9
- 238000005189 flocculation Methods 0.000 abstract description 5
- 230000016615 flocculation Effects 0.000 abstract description 5
- 230000002776 aggregation Effects 0.000 description 14
- 239000007789 gas Substances 0.000 description 11
- 238000005054 agglomeration Methods 0.000 description 7
- 238000004220 aggregation Methods 0.000 description 6
- 239000012717 electrostatic precipitator Substances 0.000 description 6
- 239000003245 coal Substances 0.000 description 5
- 230000000694 effects Effects 0.000 description 5
- 238000002485 combustion reaction Methods 0.000 description 4
- 239000010419 fine particle Substances 0.000 description 4
- 230000015271 coagulation Effects 0.000 description 3
- 238000005345 coagulation Methods 0.000 description 3
- 238000010586 diagram Methods 0.000 description 3
- 239000000615 nonconductor Substances 0.000 description 3
- 239000012716 precipitator Substances 0.000 description 3
- 239000000443 aerosol Substances 0.000 description 2
- 239000004020 conductor Substances 0.000 description 2
- 230000007423 decrease Effects 0.000 description 2
- 239000007788 liquid Substances 0.000 description 2
- 238000011144 upstream manufacturing Methods 0.000 description 2
- 230000004931 aggregating effect Effects 0.000 description 1
- 238000004887 air purification Methods 0.000 description 1
- XAGFODPZIPBFFR-UHFFFAOYSA-N aluminium Chemical compound [Al] XAGFODPZIPBFFR-UHFFFAOYSA-N 0.000 description 1
- 229910052782 aluminium Inorganic materials 0.000 description 1
- 239000004411 aluminium Substances 0.000 description 1
- 239000008280 blood Substances 0.000 description 1
- 210000004369 blood Anatomy 0.000 description 1
- 239000011362 coarse particle Substances 0.000 description 1
- 230000003247 decreasing effect Effects 0.000 description 1
- 238000005516 engineering process Methods 0.000 description 1
- 101150036577 fl11 gene Proteins 0.000 description 1
- 230000009191 jumping Effects 0.000 description 1
- 239000000463 material Substances 0.000 description 1
- 238000000746 purification Methods 0.000 description 1
- 238000011084 recovery Methods 0.000 description 1
- 230000003068 static effect Effects 0.000 description 1
Landscapes
- Electrostatic Separation (AREA)
Abstract
Description
【発明の詳細な説明】
(産業上の利用分野)
本発明は流体中の微粒子を静電力を利用して凝集・粗大
化をはかる静電′11集装置に関する。更に詳述すると
、本発明は、サブミクロン粒子を電気集塵し易いミクロ
ン以上の大きさに1i集する多1重ei電界型静電li
集装置に関する。DETAILED DESCRIPTION OF THE INVENTION (Field of Industrial Application) The present invention relates to an electrostatic concentrator that uses electrostatic force to aggregate and coarsen fine particles in a fluid. More specifically, the present invention provides a multi-layer EI electric field type electrostatic li which condenses submicron particles to a size of microns or more that is easy to electrostatically collect.
Concerning a collection device.
(従来の技術)
従来からガス流量が非常に多くかつその中に含まれる粉
塵量も多い石炭燃焼の排ガス処理には大型の電気集塵装
置が使われているが、排ガス中の粉塵はミクロン以上の
フライアッシュが中心であるため、集塵効率が高く凝集
・粗大化させる必要が少ない、従来の靜を凝集装置は、
平行な平板電極に印加する電圧を交流電圧あるいは直流
電圧とした簡単な構造のものが一般的である。(Prior technology) Large electrostatic precipitators have traditionally been used to treat the exhaust gas of coal combustion, where the gas flow rate is extremely high and the amount of dust contained therein is large. Since the main material is fly ash, the conventional flocculation equipment has high dust collection efficiency and there is little need for agglomeration and coarsening.
A simple structure in which the voltage applied to parallel plate electrodes is AC voltage or DC voltage is common.
(発明が解決しようとする課題)
ところが、最近、資源のエネルギー回収率を上げて最大
限電気エネルギーに変換するため、石炭を更に微細に砕
いて燃焼させる傾向にあり、従来の排ガスには含まれて
いなかったサブミクロンのフライアッシュとカーボンと
が多tに含まれる事態が生じている。(Problem to be solved by the invention) However, in recent years, in order to increase the energy recovery rate of resources and convert them into electrical energy as much as possible, there has been a trend toward burning coal by crushing it into even finer pieces. A situation has arisen in which a large amount of submicron fly ash and carbon, which had not been prepared before, are included.
電気抵抗の大きな不導電性のフライアッシュとこれに比
べて電気抵抗が極端に小さな導電性のカーボン粒子との
電気的性質が大きく異なる2種のサブミクロン粒子が大
量に混在しかつ大量のガス流量を伴って流入するとき、
フライアッシュ粒子の荷電址不足とカーボン粒子の跳躍
運動のため集塵率を大幅に低下させる問題が生ずる。特
に、カーボン微粒子の場合、従来の凝集装置では接地電
位の集塵板に−・時的に付着し堆積するが、接地電位の
集塵板を通じて電荷が放電し電気的吸引力を失うため、
S塵板の上でも捕集できないし凝集粒子としても安定性
が悪い問題がある。A large amount of two types of submicron particles with very different electrical properties, non-conductive fly ash with high electrical resistance and conductive carbon particles with extremely low electrical resistance, coexist and a large gas flow rate. When it flows in with
The problem arises that the dust collection rate is significantly reduced due to the insufficient charge of the fly ash particles and the jumping movement of the carbon particles. In particular, in the case of carbon fine particles, in conventional agglomeration devices, they sometimes adhere and accumulate on the dust collecting plate at ground potential, but the electric charge is discharged through the dust collecting plate at ground potential and the electric attraction is lost.
There is a problem that it cannot be collected even on an S dust plate and that the stability of aggregated particles is poor.
この排ガスの性状の変化は、微粉炭燃焼後の排ガス中に
多量に含まれるサブミクロンエアロゾルの集血効率の大
幅な低下という問題をもたらす虞がある。This change in the properties of the exhaust gas may cause a problem of a significant decrease in blood collection efficiency of submicron aerosols contained in large amounts in the exhaust gas after pulverized coal combustion.
本発明は、サブミクロン粒子を凝集させて電気4A塵し
易いミクロン以上の粒子に粗大化させる静電凝集装置を
提供することを目的とする。また、本発明は流量の多い
含塵流体に大量に含まれる電気的性質の大きく異なる2
種以上のサブミクロン粒子を同時にai4A−粗大化さ
せ得る静電1i集装置を提O(することを目的とする。SUMMARY OF THE INVENTION An object of the present invention is to provide an electrostatic agglomeration device that aggregates submicron particles and coarsens them into micron or larger particles that are easily converted to 4A dust. In addition, the present invention can also be used for two types of dust-containing fluids that have large amounts of electrical properties and that are contained in a large amount in a large amount of dust-containing fluid.
The purpose of this invention is to provide an electrostatic collector capable of simultaneously coarsening more than one species of submicron particles.
(課題を解決するための手段)
かかる目的を達成するため、本発明の多重極電界型静電
集塵装置は、荷電装置の下流fl11に、対向する複数
の平板電極とこの間に配置される複数本の棒状電極とを
含塵流体の流れに平行に配置し、前記棒状電極と平板電
極との間に交流重畳の直流高電圧を印加するようにして
いる。(Means for Solving the Problems) In order to achieve the above object, the multipole electric field type electrostatic precipitator of the present invention has a plurality of opposing flat plate electrodes disposed downstream fl11 of the charging device and a plurality of plate electrodes disposed between them. A rod-shaped electrode is arranged parallel to the flow of the dust-containing fluid, and a high DC voltage with AC superimposition is applied between the rod-shaped electrode and the plate electrode.
(作用)
したがって、電極に交流重畳の直流高電圧を荷電すれば
、高電界領域に包囲された低電界領域が含塵流体の流れ
方向に沿って電界が形成され、カーボン等の導電性粒子
は電界の中で分極を起し電界の強い部分に、あらかじめ
電荷が与えられたフライアッシュ等の不導電性粒子は電
界の弱い方即ち高電界領域に包囲さ九た低電界領域に集
まろうとする。同時に交流電界に振られるのでフライア
ッシュは電界中心の低電界領域に集まり易い。このため
、高電界による衝突凝集と不平等高電界による電界凝集
とが飛躍的に促進され、′84ii間をサブミクロン粒
子が流る間に凝集し粗大化する。そして、更に下流側に
おいて粗大化した荷電フライアッシュ粒子とカーボン粒
子とがそれらの間に顔くクーロン力によって電気力線の
支配を脱して衝突し凝集が一層促進される。同時に、直
流な界の働きによって集am能も発揮する。(Function) Therefore, if the electrode is charged with a DC high voltage with AC superimposition, an electric field is formed in the low electric field area surrounded by the high electric field area along the flow direction of the dust-containing fluid, and conductive particles such as carbon Non-conductive particles such as fly ash, which are polarized in the electric field and have been given a charge in advance in areas where the electric field is strong, tend to gather in the area where the electric field is weak, that is, surrounded by the high electric field area and the low electric field area. . At the same time, since it is shaken by an alternating electric field, fly ash tends to collect in the low electric field area at the center of the electric field. For this reason, collision aggregation due to a high electric field and electric field aggregation due to an uneven high electric field are dramatically promoted, and while submicron particles flow between '84ii, they aggregate and become coarse. Furthermore, on the downstream side, the coarsened charged fly ash particles and carbon particles collide due to the Coulomb force between them, breaking free from the control of the electric lines of force, and aggregation is further promoted. At the same time, it also exhibits am-collecting ability due to the action of the direct current field.
(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.
本発明の多重極電界型″11集装置10は、サブミクロ
ンの微粒子にあらかじめ電荷を与える荷電装置1(現有
の上流側の電気集塵器を兼用することができる)とミク
ロン以上の大きさに凝集・粗大化した粉塵を集塵する集
塵手段2(現有の下流側の電気集塵器を流用することが
できる)との間に、複数本の棒状を極3A、3B、・・
・とこれを挾むように対向す複数の平板型i4とを含塵
流体の流れに平行に配置し、前記電極棒3A、3B、・
・・と平板電極4との間に交流重畳の直流高電圧を荷電
する一方、電極の間に含塵流体を流すように構成して成
る。The multipole electric field type "11 collector 10 of the present invention has a charging device 1 (which can also be used as an existing upstream electrostatic precipitator) that charges submicron fine particles in advance, and a charging device 1 that precharges submicron fine particles. A plurality of rod-shaped poles 3A, 3B,...
- and a plurality of flat plate types i4 facing each other so as to sandwich them are arranged parallel to the flow of the dust-containing fluid, and the electrode rods 3A, 3B,
... and the flat plate electrode 4 are charged with a DC high voltage with AC superimposition, and a dust-containing fluid is caused to flow between the electrodes.
例えば、第1図に示すように、含塵流体の流れに平行に
接地電位の2枚の平板電極4とこの間に2木の棒状電極
3A、3Bを上下に配置し、棒状電極3A、3Bに交流
電圧を重畳したマイナスの直流高電圧を印加するように
している。電極3A。For example, as shown in FIG. 1, two flat plate electrodes 4 at ground potential are placed parallel to the flow of the dust-containing fluid, and two wooden rod-shaped electrodes 3A, 3B are arranged one above the other between them. A negative high DC voltage superimposed on an AC voltage is applied. Electrode 3A.
3Bは電界だけをコントロールするためのもので、コロ
ナ放電を起さない程度の太さの棒状物、例えば本実施例
の場合円筒形状が採用されている。また、平板電極4は
含塵流体例えば微粉炭燃焼排ガスを流すダクト5内に対
向させて流れに平行に設置されている0通常、この平板
電極4はダクト5とは別体で構成されているが、場合に
よってはダクト5そのものを平板電極として使用するこ
ともI7r能である。3B is for controlling only the electric field, and a rod-like object having a thickness that does not cause corona discharge, for example, in this embodiment, a cylindrical shape is adopted. Further, the flat plate electrode 4 is installed in a duct 5 in which a dust-containing fluid such as pulverized coal combustion exhaust gas flows, facing in parallel to the flow.Normally, this flat plate electrode 4 is constructed separately from the duct 5. However, depending on the case, it is also possible to use the duct 5 itself as a flat electrode.
第1図の実施例は2本の棒状電極3と2枚の平板電極4
とによって構成される4電極電界型静電凝集装置の一例
で、平板電極4から中央の棒状電極3A、3Bに向けて
出る電気力線の反発によって、高電界領域6に包囲され
る低電界領域7が中央部に広く存在するため含塵流体中
に含まれる荷電フライアッシュ粒子即ち不導体粒子の割
合の多い場合の凝集に適している。このaI集装置は含
塵流体の流量や含塵量が多い場合には、流路の縦方向及
び横方向に何組も設置するのが好ましい9例えば第1図
において仮想線で示すように図の上下方向及び左右方向
に連続的に通常何層も設けられる1、尚、第1図におい
て含塵流体の流れ方向は紙面と直交する方向である。The embodiment shown in FIG. 1 includes two rod-shaped electrodes 3 and two flat electrodes 4.
This is an example of a four-electrode electric field type electrostatic condensation device configured with a low electric field region surrounded by a high electric field region 6 due to the repulsion of electric lines of force coming out from the flat plate electrode 4 toward the central rod-shaped electrodes 3A and 3B. Since 7 is widely present in the center, it is suitable for agglomeration when a large proportion of charged fly ash particles, ie, nonconductor particles, are contained in the dust-containing fluid. When the flow rate or amount of dust contained in the dust-containing fluid is large, it is preferable to install several sets of this aI collection device in the vertical and horizontal directions of the flow path. Normally, several layers are provided continuously in the vertical and horizontal directions of 1. In FIG. 1, the flow direction of the dust-containing fluid is perpendicular to the plane of the paper.
また、第2図に3本の棒状な極3A、3B、3Cと2枚
の平板電極4とから成る5主極電界型静電11集装置を
示す。この装置はガスの流れに平行に対向設置された2
枚の平板電極4の間にガスの流れ方向に平行に3本の棒
状電極3A、3L3,3Cを一定間隔をあけて配置し、
中央の円筒電極3Cと平板型11i4を接地電位とし、
両端の棒状電極3A、3Bに交流電圧を重畳したマイナ
スの直流高電圧を荷電するようにしたものである。した
がって、電界は中央の電極3Cから両端の電極3A。Further, FIG. 2 shows a five-principal electric field type electrostatic concentrator 11 consisting of three rod-shaped poles 3A, 3B, and 3C and two flat electrodes 4. This device consists of two devices installed parallel to the gas flow and facing each other.
Three rod-shaped electrodes 3A, 3L3, 3C are arranged at regular intervals between the flat plate electrodes 4 in parallel to the gas flow direction,
The central cylindrical electrode 3C and the flat plate 11i4 are at ground potential,
The rod-shaped electrodes 3A and 3B at both ends are charged with a negative DC high voltage superimposed with an AC voltage. Therefore, the electric field extends from the central electrode 3C to the electrodes 3A at both ends.
3Bに向かう電気力線と平板電極4から両端の電IJi
3A、3Bに向かう電気力線とによって形成され、高電
界領1!A6に包囲される低電界領域7が左右に分かれ
て狭く形成されるような分布となる。Electric lines of force toward 3B and electric current IJi at both ends from the flat plate electrode 4
High electric field region 1! The distribution is such that the low electric field region 7 surrounded by A6 is divided into left and right and narrowly formed.
この場合、前述の4主極型に比べて高゛工界領域6が広
いので導電性カーホン等の導体粒子の割合の多い流体か
らの凝集に適している。この5主極型の場合、3本の棒
状電極3A、38.3Cと2枚の平板型[4によって1
組の11集装置が形成され、第1図の4電極と同様に仮
想線で示すように縦横に連続的に何層もセット可能であ
る。この場合、平板電極や棒状電極を共用することも可
能である。In this case, since the high-intensity region 6 is wider than in the above-mentioned four-principal type, it is suitable for agglomeration from a fluid containing a large proportion of conductive particles, such as a conductive carphone. In the case of this 5-main electrode type, three rod-shaped electrodes 3A, 38.3C and two flat plate type [4
A set of 11 concentrators is formed, and like the four electrodes in FIG. 1, it is possible to set many layers continuously in the vertical and horizontal directions as shown by the imaginary lines. In this case, it is also possible to share a flat plate electrode or a rod-shaped electrode.
これら凝集装置10は何段かの集塵ユニットを連結させ
た公知の大型電気集塵装置の中間段として組込まれるか
、あるいは独自に荷電装置及び集塵手段を具備する凝集
集塵装置として構成することができる0例えば、第3図
に示すように、放電極と集m電極とを1セツトとして収
容した集塵ユニットを処理ガス址に応じて何段か接続し
たものにおいて、その中間段に本発明の凝集装置10を
設置し、前段の荷電装置としての電気集塵器lにおいて
あらかじめ大径の粉塵を集塵した後、本発明の凝集装置
10においてサブミクロンの粉塵を′a集・粗大化させ
て集塵し易いミクロン以上の粒子とし、後段の集塵手段
としての電気集塵器2において捕集する。この場合、前
段の電気集塵器1においてフライアッシュ等の不導体の
サブミクロン粒子には電荷が与えられているため、凝集
装置10内の電界の働きによって粒子を衝突させti集
粗大化させる。また、カーボン等の導体粒子においては
電界内において分極し、強電界6内にaSして衝突のチ
ャンスを増して粗大化する。更に、Ij!l!電界領域
6と低電界領域7とに分かれた電気的性質の異なるフラ
イアッシュとカーボンとは、下流側に流れるに従って粗
大化してクーロン力を増し、互いのクーロン力によって
電気力線の支配から脱して衝突し、is性の安定゛した
粗大粒子に成長する。そして、後段の電気集塵器2によ
って集塵される。These coagulation devices 10 may be incorporated as an intermediate stage of a known large-scale electrostatic precipitator in which several stages of dust collection units are connected, or they may be configured as a coagulation dust collector that is independently equipped with a charging device and a dust collection means. For example, as shown in Figure 3, in a case where a dust collection unit containing a discharge electrode and a collection electrode as one set is connected in several stages depending on the processing gas area, the main stage is installed in the middle stage. The agglomerating device 10 of the present invention is installed, and after large-diameter dust is collected in advance in the electrostatic precipitator l as a charging device in the preceding stage, the submicron dust is collected and coarsened in the aggregating device 10 of the present invention. The particles are collected in an electric precipitator 2 as a subsequent dust collecting means. In this case, since the submicron particles of nonconductor such as fly ash are charged in the pre-stage electrostatic precipitator 1, the electric field in the aggregation device 10 causes the particles to collide and become coarse. Further, conductor particles such as carbon are polarized in the electric field, aS in the strong electric field 6, increasing the chance of collision, and becoming coarse. Furthermore, Ij! l! Fly ash and carbon, which are separated into the electric field region 6 and the low electric field region 7 and have different electrical properties, become coarser as they flow downstream, increasing the Coulomb force, and the Coulomb force of each other allows them to escape from the control of the electric lines of force. They collide and grow into stable IS-like coarse particles. Then, the dust is collected by the electric precipitator 2 in the latter stage.
また、独自に荷電装置と集塵手段とを!′i、01il
シて単一の静電凝集集塵ユニットを構成することも可能
である。この場合、平板電極と棒状電極の上流側に小規
模の荷電装置・放電極をa置し、後流側に集塵電極を設
けて粗大化したサブミクロン粒子を集塵する。このよう
な実施例は、サブミクロン粒子が主体を占める流体の浄
化、例えば空気清浄器、クリーンルーム用空気浄化装置
などに適用する場合に有効である。尚、棒状電極にはマ
イナスの直流高電圧が印加されているため集塵効果があ
る。We also have our own charging device and dust collection means! 'i, 01il
It is also possible to construct a single electrostatic coagulation dust collecting unit. In this case, a small-scale charging device/discharge electrode is placed on the upstream side of the flat plate electrode and the rod-shaped electrode, and a dust collection electrode is provided on the downstream side to collect coarse submicron particles. Such embodiments are effective when applied to purification of fluids mainly composed of submicron particles, such as air purifiers and clean room air purification devices. In addition, since a negative DC high voltage is applied to the rod-shaped electrode, it has a dust collection effect.
尚、本実施例においては、含塵流体として主に微粉炭燃
焼の排ガスを挙げ説明しているが、これ以外のガスは勿
論のこと、サブミクロン粒子の塵埃を含む液体特に低粘
性の液体についても適用可能である。In this example, the exhaust gas from pulverized coal combustion is mainly used as the dust-containing fluid, but other gases as well as liquids containing submicron particle dust, especially low-viscosity liquids, may be used. is also applicable.
(発明の効果)
以上の説明より明らかなように、本発明の静電凝集装置
は、含a流体の流れ方向に連続的に強電界領域とこれに
包囲される低電界領域とを形成し、あらかじめ電荷が勺
えられた不導体粒子と電界内において分極する導体粒子
とを交流電界が振られて電気力線の影響によって強電界
領域と低電界領域とに分けて集めて各々衝突させ凝集す
る一方、更にこれらが粗大化するに従って互いに保有す
るクーロン力によって電気力線の支配を脱して凝集させ
るようにしているので、電気的性質の異なる2s!以上
のサブミクロン粒子を同時に効率良く集塵できる。勿論
、不導体粒子例えばフラ、イアッシュだけを集塵する場
合にも凝集作用は劣らないので集塵効率は向上する0例
えば、サブミクロンフライアッシュについての凝集作用
実J!1例を第4図に示すと、この図から凝集装置が作
動する場合と作動してない場合に1−以下の粒子におい
て集塵効果が著しく異なることが理解できる。即ち、こ
の図からは凝集装置が作動すると粒径11JI11以下
の粒子の占める割合が減少し、凝集作用があることが理
解できる。粒径IIJ11以下の粒子の重量割合を見る
と凝集装置が不動作の場合、全体の10%に達したのが
装置を作動させると2%に減少している。尚、横軸の粒
径に対してfJ軸は大きな粒径粒子から積算した重量分
布を表す。(Effects of the Invention) As is clear from the above description, the electrostatic condensation device of the present invention continuously forms a strong electric field region and a low electric field region surrounded by the strong electric field region in the flow direction of the aluminium-containing fluid, An alternating current electric field is applied to nonconductor particles that have been charged in advance and conductor particles that are polarized in an electric field, and are separated into a strong electric field region and a low electric field region by the influence of electric lines of force, and are brought together to collide with each other and coagulate. On the other hand, as these become coarser, the Coulomb force possessed by each other causes them to escape from the control of the electric lines of force and cohere, so 2s! with different electrical properties! The above submicron particles can be collected efficiently at the same time. Of course, even when only nonconducting particles such as fly ash are collected, the flocculation effect is not inferior, so the dust collection efficiency is improved. An example is shown in FIG. 4. From this figure, it can be seen that the dust collection effect for particles of 1 or less is significantly different when the aggregation device is activated and when it is not activated. That is, it can be seen from this figure that when the agglomeration device operates, the proportion of particles with a particle size of 11JI11 or less decreases, and there is an aggregation effect. Looking at the weight percentage of particles with a particle size of IIJ11 or less, when the agglomeration device was not in operation, it reached 10% of the total, but when the device was in operation, it decreased to 2%. It should be noted that the fJ axis represents the weight distribution integrated from particles with a large particle size with respect to the particle size on the horizontal axis.
4、図面のff1jlNな説明
第1図及び第2図は本発明の多重極電界型静電凝集装置
の一例を示すものが、第1図は4平極電界型静電凝集装
置の一例を示す概略原理図、第2図は5電極電界型静電
11集装置の一例を示す概略原理図である。第3図は本
発明の多71Ltf!電界型静@凝集装置を大型集塵器
に組込む場合の概略図、第4図は第1図の4電極電界型
静電″a集装貢を作動させた場合と作動させない場合の
電気集a 2iSの出口におけるエアロゾル粒子の粒径
分布を示すグラフである。4. Explanation of drawings Figures 1 and 2 show an example of a multi-pole electric field type electrostatic condensation device of the present invention, and Figure 1 shows an example of a 4-plane electric field type electrostatic condensation device. Schematic Principle Diagram: FIG. 2 is a schematic principle diagram showing an example of a five-electrode electric field type electrostatic 11 concentrator. FIG. 3 shows the multi-71Ltf! of the present invention! A schematic diagram of the case where an electric field type static @ agglomeration device is incorporated into a large precipitator. Figure 4 shows the electric field collector a with and without the 4-electrode electric field type electrostatic concentrator in Figure 1 activated. 2 is a graph showing the particle size distribution of aerosol particles at the exit of 2iS.
1・・・荷電装置、2・・・集塵装置、3・・・棒状電
極、4・・・平板電極、5・・・ダクト、6・・・強電
界領域、7・・・低電界領域。DESCRIPTION OF SYMBOLS 1... Charging device, 2... Dust collector, 3... Rod-shaped electrode, 4... Flat electrode, 5... Duct, 6... Strong electric field region, 7... Low electric field region .
特許用雇人 財団法人 電力中央研究所第4図 粒 径(−)Patent employee: Central Research Institute of Electric Power Industry, Figure 4 Particle diameter (-)
Claims (1)
に配置される複数本の棒状電極とを含塵流体の流れに平
行に配置し、前記棒状電極と平板電極との間に交流重畳
の直流高電圧を印加することを特徴とする多重極電界型
静電凝集装置。On the downstream side of the charging device, a plurality of opposing flat plate electrodes and a plurality of rod-shaped electrodes arranged between them are arranged parallel to the flow of the dust-containing fluid, and a superimposed alternating current is generated between the rod-shaped electrodes and the flat plate electrode. A multipole electric field type electrostatic condensation device that applies a high DC voltage.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP63128243A JPH01299647A (en) | 1988-05-27 | 1988-05-27 | Multiple electric field-type electrostatic fluocculator |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP63128243A JPH01299647A (en) | 1988-05-27 | 1988-05-27 | Multiple electric field-type electrostatic fluocculator |
Publications (1)
Publication Number | Publication Date |
---|---|
JPH01299647A true JPH01299647A (en) | 1989-12-04 |
Family
ID=14980037
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
JP63128243A Pending JPH01299647A (en) | 1988-05-27 | 1988-05-27 | Multiple electric field-type electrostatic fluocculator |
Country Status (1)
Country | Link |
---|---|
JP (1) | JPH01299647A (en) |
Cited By (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN112076892A (en) * | 2019-06-14 | 2020-12-15 | 釜山大学校产学协力团 | Electric dust removal device and air purification device adopting same |
-
1988
- 1988-05-27 JP JP63128243A patent/JPH01299647A/en active Pending
Cited By (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN112076892A (en) * | 2019-06-14 | 2020-12-15 | 釜山大学校产学协力团 | Electric dust removal device and air purification device adopting same |
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