WO2019138922A1 - 電気集塵装置 - Google Patents
電気集塵装置 Download PDFInfo
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- WO2019138922A1 WO2019138922A1 PCT/JP2018/048401 JP2018048401W WO2019138922A1 WO 2019138922 A1 WO2019138922 A1 WO 2019138922A1 JP 2018048401 W JP2018048401 W JP 2018048401W WO 2019138922 A1 WO2019138922 A1 WO 2019138922A1
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- WIPO (PCT)
- Prior art keywords
- dust collection
- electrode
- dust
- collection electrode
- ion wind
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B03—SEPARATION 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
- B03C—MAGNETIC OR ELECTROSTATIC SEPARATION OF SOLID MATERIALS FROM SOLID MATERIALS OR FLUIDS; SEPARATION BY HIGH-VOLTAGE ELECTRIC FIELDS
- B03C3/00—Separating dispersed particles from gases or vapour, e.g. air, by electrostatic effect
- B03C3/02—Plant or installations having external electricity supply
- B03C3/04—Plant or installations having external electricity supply dry type
- B03C3/06—Plant or installations having external electricity supply dry type characterised by presence of stationary tube electrodes
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B03—SEPARATION 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
- B03C—MAGNETIC OR ELECTROSTATIC SEPARATION OF SOLID MATERIALS FROM SOLID MATERIALS OR FLUIDS; SEPARATION BY HIGH-VOLTAGE ELECTRIC FIELDS
- B03C3/00—Separating dispersed particles from gases or vapour, e.g. air, by electrostatic effect
- B03C3/34—Constructional details or accessories or operation thereof
- B03C3/40—Electrode constructions
- B03C3/41—Ionising-electrodes
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B03—SEPARATION 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
- B03C—MAGNETIC OR ELECTROSTATIC SEPARATION OF SOLID MATERIALS FROM SOLID MATERIALS OR FLUIDS; SEPARATION BY HIGH-VOLTAGE ELECTRIC FIELDS
- B03C3/00—Separating dispersed particles from gases or vapour, e.g. air, by electrostatic effect
- B03C3/34—Constructional details or accessories or operation thereof
- B03C3/40—Electrode constructions
- B03C3/45—Collecting-electrodes
- B03C3/49—Collecting-electrodes tubular
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B03—SEPARATION 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
- B03C—MAGNETIC OR ELECTROSTATIC SEPARATION OF SOLID MATERIALS FROM SOLID MATERIALS OR FLUIDS; SEPARATION BY HIGH-VOLTAGE ELECTRIC FIELDS
- B03C3/00—Separating dispersed particles from gases or vapour, e.g. air, by electrostatic effect
- B03C3/34—Constructional details or accessories or operation thereof
- B03C3/74—Cleaning the electrodes
- B03C3/76—Cleaning the electrodes by using a mechanical vibrator, e.g. rapping gear ; by using impact
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B03—SEPARATION 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
- B03C—MAGNETIC OR ELECTROSTATIC SEPARATION OF SOLID MATERIALS FROM SOLID MATERIALS OR FLUIDS; SEPARATION BY HIGH-VOLTAGE ELECTRIC FIELDS
- B03C3/00—Separating dispersed particles from gases or vapour, e.g. air, by electrostatic effect
- B03C3/34—Constructional details or accessories or operation thereof
- B03C3/74—Cleaning the electrodes
- B03C3/78—Cleaning the electrodes by washing
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B03—SEPARATION 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
- B03C—MAGNETIC OR ELECTROSTATIC SEPARATION OF SOLID MATERIALS FROM SOLID MATERIALS OR FLUIDS; SEPARATION BY HIGH-VOLTAGE ELECTRIC FIELDS
- B03C2201/00—Details of magnetic or electrostatic separation
- B03C2201/10—Ionising electrode has multiple serrated ends or parts
Definitions
- the present disclosure relates to an electrostatic precipitator.
- an electrostatic precipitator including a flat dust collecting electrode arranged in parallel along a gas flow and a discharge electrode having a sharp shape arranged at the center thereof.
- a high DC voltage is applied between the dust collection electrode and the discharge electrode to perform stable corona discharge on the discharge electrode, thereby charging dust in the gas flow.
- charged dust is collected at the dust collection electrode by the action of the Coulomb force acting on the dust under an electric field between the discharge electrode and the dust collection electrode.
- the electrostatic precipitator of patent documents 1 and 2 is provided with a plurality of penetration holes for letting dust pass, and is provided with a dust collection pole which had a closed space for collecting dust inside.
- trapped dust is less likely to be scattered again by confining the dust in the closed space via the through holes.
- the electrostatic precipitator of Patent Document 3 includes a dust collection electrode including an earth electrode having an opening ratio of 65% to 85%, and a dust collection filter layer for collecting dust.
- a dust collection electrode including an earth electrode having an opening ratio of 65% to 85%
- a dust collection filter layer for collecting dust.
- Patent No. 5761461 gazette Patent No. 5705461 gazette Patent No. 4823691
- the dust collection efficiency ⁇ in the electrostatic precipitator can be calculated by the well-known German equation (equation (1)) below.
- w a dust collection index (moving speed of particulate matter)
- f a dust collection area per unit gas amount.
- ⁇ 1-exp (-w ⁇ f) (1)
- the moving speed w of the dust is determined to be determined by the relationship between the Coulomb force and the viscous drag of the gas.
- dust is said to move from the discharge electrode in the electric field, and the ion wind is not directly considered in the influence on performance.
- the dust concentration which is the premise of its performance design, has the precondition that it is always uniform in the dust collection space between the discharge electrode and the dust collection electrode, and the ion wind causes gas turbulence, It is considered as one of the factors that make the dust concentration uniform.
- the ion wind generates negative ions by corona discharge at the discharge electrode when a negative voltage is applied between the electrodes, and as a result, it is generated by positive ions in the case of a positive voltage.
- a negative voltage is described in order to consider the industrial electrostatic precipitator as a base, but the same is true even if it is positive.
- the ion wind generated by the discharge electrode flows across the gas flow toward the dust collection electrode.
- the ion wind that has reached the collecting electrode is reversed at the collecting electrode to change the flow direction. This causes a helical turbulence between the electrodes.
- the flow from the discharge electrode to the dust collection electrode has an effect of carrying dust to the vicinity of the dust collection electrode.
- the dust carried to the vicinity of the dust collection electrode is finally collected by the Coulomb force.
- Patent Document 3 describes an electrostatic precipitator in consideration of the effect of ion wind.
- the structure is such that the ion wind is sent to the filter layer behind the dust collection electrode having the opening, and the structure is complicated in order to collect dust in a region not affected by the main gas. In some cases, it was difficult to separate and collect dust attached to the filter layer in the dry state.
- the present disclosure has been made in view of such circumstances, and it is an object of the present invention to provide an electrostatic precipitator capable of suppressing the separation effect of ion wind which reduces the dust collection effect and enhancing the dust collection efficiency. To aim.
- An electrostatic precipitator has a plurality of dust collection poles which are formed in a columnar shape and which are disposed at predetermined intervals in an orthogonal direction orthogonal to the longitudinal direction, and the dust collection electrode side A plurality of discharge parts protruding and arranged in parallel with the orthogonal direction are provided, and the equivalent diameter of the cross section of the dust collection electrode is 30 mm or more and 80 mm or less.
- the equivalent diameter of the cross section of the dust collection electrode was 30 mm or more. When the equivalent diameter is reduced, the concentration of the electric field is increased and the dust collection property is enhanced. However, if the equivalent diameter is too small, the peak value of the electric field strength becomes large and spark discharge occurs while maintaining the current necessary for dust collection. For this reason, the lower limit as an equivalent diameter is 30 mm.
- the equivalent diameter of the cross section of the dust collection electrode was 80 mm or less.
- equivalent diameter When the equivalent diameter is too large, the lifting of the electric field intensity in the vicinity of the dust collection electrode is hardly caused, and the average electric field intensity of the flat plate electrode will be about. In addition, if the equivalent diameter is large, a swirl is generated to the gas flow. For this reason, the upper limit as an equivalent diameter is 80 mm.
- equivalent diameter is meant a circular diameter equivalent to the cross section of a given shape. Thus, if the cross-section is circular, this corresponds to its diameter.
- the dust collection electrode for example, a pipe-shaped member having a circular cross section can be mentioned. However, as the cross-sectional shape, in addition to the circular shape, an oval, an oval, a polygon or the like is used.
- not only hollow but also solid may be used as a dust collection electrode.
- the flow direction of the gas flowing through the electrostatic precipitator may be an orthogonal direction in which the dust collection electrodes are arranged, or may be a longitudinal direction of the dust collection electrodes.
- the dust collection electrode can be separated and recovered from dust due to beating, a method of moving the dust collection electrode and scraping the dust with a brush, or wet cleaning.
- the aperture ratio of the dust collection electrode disposed at a predetermined interval is set to 10% or more and 70% or less.
- the one and the other discharge parts are respectively disposed on both sides of the dust collection electrode arranged in the orthogonal direction, and the discharge part from the one discharge part It is arrange
- FIG. 1 is a perspective view showing an electrostatic precipitator according to an embodiment of the present disclosure. It is the top view which looked at the electrostatic precipitator of FIG. 1 from upper direction. It is the front view which looked at the electrostatic precipitator of FIG. 1 from the gas flow direction. It is the front view which showed the modification of FIG. It is a cross-sectional view which showed the positional relationship of a dust collection pole and a projection part. It is a cross-sectional view which showed the electric line of force between a projection part and a dust collection pole. It is a graph which shows a ground which set the lower limit of the equivalent diameter of a dust collection pole to 30 mm. It is a graph which shows the ground which made the upper limit of the equivalent diameter of a dust collection pole 80 mm.
- the electrostatic precipitator 1 is used, for example, in a thermal power plant using coal as a fuel, and recovers dust (particulate matter) in combustion exhaust gas led from a boiler.
- the electrostatic precipitator 1 includes, for example, a plurality of conductive dust collectors 4 made of metal or the like.
- the dust collection electrode 4 is a hollow column shaped circular pipe having a circular cross section, and is arranged at a predetermined interval in the orthogonal direction (the gas flow G direction) orthogonal to the longitudinal direction.
- a plurality of dust collection electrode 4 rows arranged in the gas flow G direction are provided in parallel at predetermined intervals.
- a discharge electrode 5 is disposed between each row of dust collection electrodes 4. In FIG. 1, the position where the discharge electrode 5 is disposed is indicated by a broken line.
- the dust collection electrode 4 is grounded.
- the discharge electrode 5 is connected to a power supply having a negative polarity (not shown).
- the power supply connected to the discharge electrode 5 may have positive polarity.
- the discharge electrode 5 is provided with a plurality of protruding portions (discharge portions) 5 a in the form of spikes.
- the protruding portion 5 a is provided so as to protrude toward the dust collecting electrode 4 with its tip end. Corona discharge is generated in the protrusion 5a, and ion wind is generated from the tip of the protrusion 5a toward the dust collection electrode 4 side.
- FIG. 1 The front view which looked at FIG. 1 from the gas flow G direction is shown by FIG.
- the protrusions 5a are provided so that the directions of the protrusions are different (directions different in the left and right directions in the figure). Then, the protrusions 5a corresponding to the same height sandwich the dust collection electrode 4 and project in the same direction.
- the protrusions 5a By arranging the protrusions 5a in this manner, the ion wind directed from the protrusions 5a toward the dust collection electrode 4 is directed in substantially the same direction in the height direction. This makes it possible to avoid ion wind interference.
- the direction of the ion wind may be aligned by directing all the protrusions 5a in the same direction (right direction in the same drawing).
- FIG. 5 is a cross-sectional view shown by cutting at the position of the protrusion 5 a at a certain height position in the configuration shown in FIG. 2. Therefore, as shown in FIG. 2 in plan view, the protrusions 5a do not appear on both sides, and only the protrusions 5a facing only one side are shown.
- Reference symbol D shown in FIG. 5 is a distance in the orthogonal direction (vertical direction in FIG. 5) between the dust collection electrode 4 and the protrusion 5a, and is, for example, 125 mm to 250 mm.
- the opening ratio ⁇ when the dust collection electrode 4 is viewed in front from the protrusion 5 a side is represented as follows, considering that the lines of electric force reach the depth of the dust collection electrode 4 as described above.
- ⁇ 1 ⁇ ((d ⁇ 3.14 ⁇ 2) ⁇ Pc) ⁇ 100 [%]
- d is the equivalent diameter of the dust collection electrode 4.
- equivalent diameter is meant the diameter of a circle (having the same area) equivalent to the cross section of a given shape. Therefore, in the case where the cross section of the dust collection electrode 4 is circular as in the present embodiment, this corresponds to the diameter thereof.
- the aperture ratio ⁇ is set to 10% or more and 70% or less. The ground will be described later with reference to FIG.
- the equivalent diameter d of the dust collection electrode 4 is 30 mm or more and 80 mm or less.
- the reason why the equivalent diameter d of the cross section of the dust collection electrode 4 is 30 mm or more is as follows.
- the equivalent diameter d is reduced, the concentration of the electric field is increased and the dust collection property is enhanced.
- the equivalent diameter d becomes too small, as shown in FIG. 7, the peak value of the electric field strength becomes large and the spark electric field strength if the current density (for example, 0.3 mA / m 2 ) necessary for dust collection is maintained. Spark discharge occurs over 10kV / cm of Therefore, the lower limit of the equivalent diameter d is 30 mm.
- the equivalent diameter d of the cross section of the dust collection electrode 4 is 80 mm or less is as follows.
- the equivalent diameter d becomes too large, the lifting of the electric field strength in the vicinity of the dust collection electrode 4 (described later with reference to FIG. 9) is almost eliminated, and the average electric field strength (2 kV / cm) of the flat plate electrode without holes become.
- the upper limit of the equivalent diameter d is 80 mm.
- the average electric field strength when the equivalent diameter d is 30 mm calculated under the same conditions as described above is about 5.7 kV / cm.
- the average electric field strength is the electric field strength averaged over the surface area of the dust collection electrode 4. This average electric field strength is different from the peak electric field strength on the vertical axis of FIG.
- the peak electric field strength is the electric field strength at the position of the highest electric field strength on the surface of the dust collection electrode 4.
- the horizontal axis indicates the position, and it is assumed that the protrusion 5a is located at the position corresponding to the y axis.
- the vertical axis is the electric field strength.
- the electric field strength is highest at the position of the protrusion 5 a and, after having a local minimum value with the dust collection electrode 4, increases toward the dust collection electrode 4 again.
- the region B where the rate of increase (inclination) of the electric field strength is large. This is because the electric field strength in the vicinity of the dust collection electrode 4 becomes high due to the space charge of dust and negative ions.
- the increase of the electric field strength in the region B is referred to as "lift of the electric field strength".
- the Coulomb force is dominant, and dust collection in the dust collection electrode 4 is effectively performed.
- the region A closer to the protrusion 5 a than the region B is considered as the dominant region of the ion wind.
- the dust P in the gas is guided to the dust collection electrode 4 mainly along with the ion wind while receiving Coulomb force.
- FIG. 10 shows, as a reference example, the electric field strength in the case of using a flat plate electrode 7 without holes as a conventional collection electrode as a dust collection electrode.
- the absolute value of the electric field intensity in the vicinity of the flat plate electrode 7 is smaller than that of the dust collection electrode 4 in the form of a circular pipe shown in FIG. Therefore, it is understood that the dust collection performance is inferior to that of the dust collection electrode 4 which is a circular pipe.
- FIG. 11 shows the dust collection area ratio to the opening ratio ⁇ .
- the dust collection area ratio indicates the dust collection area when the same dust collection performance is exhibited when the dust collection performance when the opening ratio is 0% (when there is no gap) is 1. Therefore, the smaller the dust collection area ratio, the higher the collection efficiency.
- the dust collection area ratio is 0.8 or less when the opening ratio ⁇ is 10% or more and 70% or less. Therefore, the aperture ratio ⁇ is preferably 10% to 70% (application range).
- the operation of the electrostatic precipitator 1 of the present embodiment will be described.
- the electrostatic precipitator 1 by applying a negative voltage to the discharge electrode 5 from the power supply, corona discharge occurs at the tip of the protrusion 5a.
- the dust contained in the gas stream G is charged by corona discharge.
- charged dust is attracted to the grounded collection electrode 4 by the Coulomb force, and is collected on the collection electrode 4, but in practice The effect of the ion wind is greatly acting.
- the dust collection electrode 4 in the form of a circular pipe at a predetermined interval, a part of the ion wind flowing from the projection 5 a toward the collection electrode 4 is dropped to the back side of the collection electrode 4 Allow As a result, the flow of ion wind reversed and separated at the dust collection electrode 4 can be suppressed, so that the collection efficiency is improved.
- a part of the ion wind flowing toward the dust collection electrode 4 including dust passes through between the dust collection electrodes 4.
- the ion wind is directed in one direction and does not interfere with each other.
- the dust collected by the dust collection electrode 4 is separated and recovered by striking.
- a method of moving the dust collection electrode and scraping off the dust with a brush, or wet cleaning may be employed.
- the following effects are achieved.
- a part of the ion wind flowing from the protrusion 5 a toward the collection electrode 4 is allowed to escape to the back side of the collection electrode 4 Do.
- the flow which ion wind reverses and separates by the dust collection pole 4 can be suppressed.
- the equivalent diameter d of the cross section of the dust collection electrode 4 was 30 mm or more and 80 mm or less. Thereby, the dust collection performance of the dust collection electrode 4 can be improved.
- the aperture ratio ⁇ is set to 10% or more and 70% or less. Thereby, an effective dust collection area can be ensured and dust collection performance can be improved.
- the ion wind generated from the projections 5a installed at the same height is directed in one direction so as not to interfere with the ion wind generated from the projections 5a set at other heights (FIG. 3). reference). Thereby, it can suppress that dust collection is inhibited by ion wind.
- the direction of the gas flow G is orthogonal to the longitudinal direction of the dust collection electrode 4, but as shown in FIG. 12, the direction of the gas flow G may be the longitudinal direction of the dust collection electrode 4 good.
- the pitch Pc of the dust collection electrode 4 and the pitch Pd of the protrusion 5a are described to be equal, but as shown in FIG. 13, the pitch Pc of the dust collection electrode 4 is greater than the pitch Pd of the protrusion 5a It may be small. In this case, it is preferable to arrange the dust collection electrodes 4 so that the electric lines of force are equally distributed as much as possible.
- the dust collection electrode 4 has been described as a circular pipe, but the cross sectional shape of the dust collection electrode 4 may be an oval, an oval, or a polygon other than a circle. Also, the dust collection electrode 4 may be a solid instead of a hollow such as a pipe.
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Abstract
Description
η=1-exp(-w×f)・・・(1)
集塵極の横断面の等価直径を30mm以上とした。等価直径を小さくすると電界集中が大きくなり集塵性は高まる。しかし、等価直径が小さくなりすぎると、集塵に必要な電流を確保したままでは電界強度のピーク値が大きくなり火花放電が生じる。このため、等価直径としての下限は30mmである。
集塵極の横断面の等価直径を80mm以下とした。等価直径が大きくなりすぎると、集塵極近傍における電界強度の持ち上がりが殆どなくなり、平板電極の平均電界強度程度になってしまう。また、等価直径が大きいとガス流れに対して渦を発生させてしまう。このため、等価直径としての上限は80mmである。
等価直径とは、所定形状の横断面と等価な円形の直径を意味する。したがって、横断面が円形の場合は、その直径に相当する。
集塵極としては、例えば円形断面とされたパイプ形状の部材が挙げられる。ただし、横断面形状としては、円形以外には、長円形、楕円形、多角形などが用いられる。また、集塵極としては中空だけでなく中実としても良い。
電気集塵装置を流れるガスの流れ方向は、集塵極が並べられた直交方向でも良いし、集塵極の長手方向でも良い。
集塵極は、槌打によるダストの剥離回収や、集塵極を移動させてブラシでダストを掻き落とす方式や、湿式洗浄も可能である。
開口率αは、等価直径をd、集塵極の中心間ピッチをPcとすると、以下のように表される。
α=1-((d×3.14÷2)÷Pc)×100 [%]
なお、図4に示すように、すべての突起部5aを同一方向(同図では右方向)に向くようにして、イオン風の方向を揃えるようにしても良い。
α=1-((d×3.14÷2)÷Pc)×100 [%]
ここで、dは集塵極4の等価直径である。等価直径とは、所定形状の横断面と等価な(同一面積を有する)円形の直径を意味する。したがって、本実施形態のように集塵極4の横断面が円形の場合は、その直径に相当する。
開口率αは、10%以上70%以下とされている。その根拠については、後に図11を用いて説明する。
集塵極4の横断面の等価直径dを30mm以上とした理由は以下の通りである。等価直径dを小さくすると電界集中が大きくなり集塵性は高まる。しかし、等価直径dが小さくなりすぎると、図7に示すように、集塵に必要な電流密度(例えば0.3mA/m2)を確保したままでは電界強度のピーク値が大きくなり火花電界強度の10kV/cmを超えて火花放電が生じる。このため、等価直径dとしての下限は30mmである。
なお、図8の縦軸は平均電界強度とされており、集塵極4の表面積で平均化した電界強度である。この平均電界強度は、図7の縦軸のピーク電界強度とは異なる。ピーク電界強度は、集塵極4の表面のうち最も電界強度が高い位置における電界強度である。
電気集塵装置1では、放電極5に電源から負電圧を印加することで、突起部5aの先端でコロナ放電が発生する。ガス流れGに含まれるダストは、コロナ放電により帯電される。従来の電気集塵装置の捕集原理では、帯電されたダストは、クーロン力により接地された集塵極4に引き寄せられ、集塵極4上に捕集されるとされてきたが、実際にはイオン風の影響が大きく作用している。
円形パイプとされた集塵極4を所定の間隔をあけて配置することで、突起部5aから集塵極4へ向けて流れるイオン風の一部が集塵極4の裏側へ抜けることを許容する。これにより、イオン風が集塵極4で反転されて離反する流れを抑制できる。
図1では、ガス流れGの方向が、集塵極4の長手方向に直交するようになっていたが、図12に示すように、ガス流れGの方向を集塵極4の長手方向としても良い。
4 集塵極
5 放電極
5a 突起部(放電部)
7 平板電極
α 開口率
d 等価直径
Claims (3)
- 柱状とされ、その長手方向に対して直交する直交方向に所定の間隔をあけて配置された複数の集塵極と、
前記集塵極側に突出し、前記直交方向と平行に並んで配置された複数の放電部と、
を備え、
前記集塵極の横断面の等価直径は、30mm以上80mm以下とされている電気集塵装置。 - 所定の間隔をあけて配置された前記集塵極の開口率が、10%以上70%以下とされている請求項1に記載の電気集塵装置。
- 一方と他方の前記放電部が、前記直交方向に並べられた前記集塵極の両側にそれぞれ配置され、
前記一方の前記放電部から前記集塵極に向かうイオン風が、前記他方の放電部から前記集塵極に向かうイオン風と対向しないように配置されている請求項1又は2に記載の電気集塵装置。
Priority Applications (9)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN201880086536.6A CN111655378A (zh) | 2018-01-15 | 2018-12-28 | 电集尘装置 |
EP18899145.9A EP3725412A4 (en) | 2018-01-15 | 2018-12-28 | ELECTROSTATIC SEPARATOR |
RU2020122679A RU2020122679A (ru) | 2018-01-15 | 2018-12-28 | Электростатический осадитель |
KR1020207020133A KR102451222B1 (ko) | 2018-01-15 | 2018-12-28 | 전기 집진 장치 |
BR112020014230-1A BR112020014230B1 (pt) | 2018-01-15 | 2018-12-28 | Precipitador eletrostático |
MX2020007386A MX2020007386A (es) | 2018-01-15 | 2018-12-28 | Precipitador electrostatico. |
US16/961,772 US11484890B2 (en) | 2018-01-15 | 2018-12-28 | Electrostatic precipitator |
PH12020500599A PH12020500599A1 (en) | 2018-01-15 | 2020-07-09 | Electrostatic precipitator |
ZA2020/04322A ZA202004322B (en) | 2018-01-15 | 2020-07-14 | Electrostatic precipitator |
Applications Claiming Priority (2)
Application Number | Priority Date | Filing Date | Title |
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JP2018-004364 | 2018-01-15 | ||
JP2018004364A JP7109194B2 (ja) | 2018-01-15 | 2018-01-15 | 電気集塵装置 |
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US (1) | US11484890B2 (ja) |
EP (1) | EP3725412A4 (ja) |
JP (1) | JP7109194B2 (ja) |
KR (1) | KR102451222B1 (ja) |
CN (1) | CN111655378A (ja) |
MX (1) | MX2020007386A (ja) |
PH (1) | PH12020500599A1 (ja) |
RU (1) | RU2020122679A (ja) |
TW (1) | TWI701079B (ja) |
WO (1) | WO2019138922A1 (ja) |
ZA (1) | ZA202004322B (ja) |
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JP7358216B2 (ja) * | 2019-11-29 | 2023-10-10 | 三菱重工パワー環境ソリューション株式会社 | 電気集塵装置 |
KR102187115B1 (ko) * | 2020-05-18 | 2020-12-04 | 주식회사 케네스 | 양방향 집진이 가능한 전기집진장치 |
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2018
- 2018-01-15 JP JP2018004364A patent/JP7109194B2/ja active Active
- 2018-12-28 KR KR1020207020133A patent/KR102451222B1/ko active IP Right Grant
- 2018-12-28 US US16/961,772 patent/US11484890B2/en active Active
- 2018-12-28 EP EP18899145.9A patent/EP3725412A4/en active Pending
- 2018-12-28 RU RU2020122679A patent/RU2020122679A/ru unknown
- 2018-12-28 WO PCT/JP2018/048401 patent/WO2019138922A1/ja active Application Filing
- 2018-12-28 CN CN201880086536.6A patent/CN111655378A/zh active Pending
- 2018-12-28 MX MX2020007386A patent/MX2020007386A/es unknown
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2019
- 2019-01-04 TW TW108100290A patent/TWI701079B/zh active
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2020
- 2020-07-09 PH PH12020500599A patent/PH12020500599A1/en unknown
- 2020-07-14 ZA ZA2020/04322A patent/ZA202004322B/en unknown
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JPS5761461B2 (ja) | 1975-03-14 | 1982-12-24 | Sanyo Electric Co | |
JPS575461B2 (ja) | 1977-05-31 | 1982-01-30 | ||
JPS627456A (ja) * | 1985-07-04 | 1987-01-14 | Takahide Ono | 電気集塵装置 |
JP2011161329A (ja) * | 2010-02-05 | 2011-08-25 | Nippon Steel Corp | 焼結機排ガスの処理装置 |
JP2016073954A (ja) * | 2014-10-08 | 2016-05-12 | 三菱日立パワーシステムズ環境ソリューション株式会社 | 電気集じん装置 |
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Also Published As
Publication number | Publication date |
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JP7109194B2 (ja) | 2022-07-29 |
PH12020500599A1 (en) | 2021-05-17 |
KR102451222B1 (ko) | 2022-10-06 |
CN111655378A (zh) | 2020-09-11 |
MX2020007386A (es) | 2020-10-05 |
BR112020014230A2 (pt) | 2020-12-01 |
US20210060578A1 (en) | 2021-03-04 |
TWI701079B (zh) | 2020-08-11 |
KR20200094210A (ko) | 2020-08-06 |
RU2020122679A (ru) | 2022-02-17 |
EP3725412A1 (en) | 2020-10-21 |
EP3725412A4 (en) | 2021-01-20 |
ZA202004322B (en) | 2021-09-29 |
JP2019122909A (ja) | 2019-07-25 |
TW201932193A (zh) | 2019-08-16 |
RU2020122679A3 (ja) | 2022-02-17 |
US11484890B2 (en) | 2022-11-01 |
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