CN103128001A - Dry-wet combination type electrostatic dust extractor and dust extracting method - Google Patents

Dry-wet combination type electrostatic dust extractor and dust extracting method Download PDF

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CN103128001A
CN103128001A CN2012104970633A CN201210497063A CN103128001A CN 103128001 A CN103128001 A CN 103128001A CN 2012104970633 A CN2012104970633 A CN 2012104970633A CN 201210497063 A CN201210497063 A CN 201210497063A CN 103128001 A CN103128001 A CN 103128001A
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dust
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李水清
靳星
杨萌萌
朱润孺
姚强
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Tsinghua University
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Abstract

本发明涉及一种针对脱除烟气中细颗粒物的干湿结合式静电除尘器及除尘方法,属于工业除尘技术领域。本发明采用现有的电除尘器,并对电场的后两级进行改造。所述除尘器的倒数第二级电场采用角钢长芒刺线、锯齿线或鱼骨型极线,增强倒数第二级电场对颗粒的荷电效果;除尘器的末级电场采用圆极线,增强末级电场的工作电压,形成强迁移电场,并减少电晕风对流场的影响;倒数第二级电场与末级电场的组合,提升了粒径在0.1-1μm的颗粒在末级电场的迁移率;在末级电场的极板上方设置若干个末级清灰喷水器,用水冲洗极板的方式取代振打清灰,确保附着在极板上的颗粒都可被清除,减小原来因振打导致的二次扬尘。

Figure 201210497063

The invention relates to a dry-wet combined electrostatic dust collector and a dust removal method aimed at removing fine particles in flue gas, belonging to the technical field of industrial dust removal. The present invention adopts the existing electric precipitator and reforms the last two stages of the electric field. The penultimate electric field of the dust collector adopts angle steel long burr wire, zigzag wire or herringbone pole line to enhance the charging effect of the penultimate electric field on the particles; the final electric field of the dust collector adopts a circular pole line, Enhance the working voltage of the final electric field, form a strong migration electric field, and reduce the influence of corona wind on the flow field; the combination of the penultimate electric field and the final electric field improves the particle size of 0.1-1μm in the final electric field Mobility; several last-stage ash-cleaning sprinklers are installed above the polar plate of the final electric field, and the method of washing the plate with water replaces vibration cleaning to ensure that the particles attached to the plate can be removed and reduce The original secondary dust caused by rapping.

Figure 201210497063

Description

一种干湿结合式静电除尘器及除尘方法A dry-wet combined electrostatic precipitator and dust removal method

技术领域 technical field

本发明涉及一种针对脱除烟气中细颗粒物的干湿结合式静电除尘器及除尘方法,属于工业除尘技术领域。  The invention relates to a dry-wet combined electrostatic dust collector and a dust removal method aimed at removing fine particles in flue gas, belonging to the technical field of industrial dust removal. the

背景技术   Background technique

煤炭是我国发电、金属冶炼、水泥制造等工业生产的主要能源,在未来几十年内依然会占据主导地位。其燃烧排放的烟气中含有大量的颗粒物,会造成严重的环境污染,特别是空气动力学直径小于2.5μm的可入肺颗粒物,它能够从呼吸道进入人体内,而且表面易富集大量重金属,对人体健康危害很大。  Coal is the main energy source for industrial production such as power generation, metal smelting, and cement manufacturing in my country, and it will still occupy a dominant position in the next few decades. The flue gas emitted by its combustion contains a large amount of particles, which will cause serious environmental pollution, especially the particles that can enter the lungs with an aerodynamic diameter of less than 2.5 μm, which can enter the human body from the respiratory tract, and the surface is easy to accumulate a large amount of heavy metals. It is very harmful to human health. the

随着环保标准不断严格,现在应用的除尘设备中只有电除尘器和布袋除尘器能够达到排放要求。其中电除尘技术具有分离作用力集中、气流阻力小、耗电少、处理规模大、耐高温和耐强腐的特点,在我国的工业生产中应用十分广泛。但其对粒径在0.1-1.0μm范围内的颗粒存在穿透窗口,分级除尘效率低于80%。其主要原因在于此粒径范围内的颗粒难以荷电,而且在振打清灰过程中颗粒容易随流,造成二次扬尘。  With the increasingly stringent environmental protection standards, only the electrostatic precipitator and bag filter can meet the emission requirements among the dust removal equipment currently in use. Among them, the electrostatic precipitator technology has the characteristics of concentrated separation force, small airflow resistance, low power consumption, large processing scale, high temperature resistance and strong corrosion resistance, and is widely used in my country's industrial production. However, it has a penetration window for particles with a particle size in the range of 0.1-1.0 μm, and the classification dust removal efficiency is lower than 80%. The main reason is that the particles in this particle size range are difficult to charge, and the particles are easy to follow the flow during the vibration cleaning process, causing secondary dust. the

针对PM2.5脱除效率不高的问题,现有的电除尘器改进方式主要有优化传统电除尘器的几何参数、运行参数,采用预凝并原理通过双极荷电使颗粒团聚,以及通过采用移动式极板、湿式电除尘器等改进清灰过程。Ohio大学采用覆膜湿式电除尘器,用纤维材料取代不锈钢板,并在极板表面形成水膜,可以大幅减少钢材的使用,并减少二次扬尘。(Membrane-based wet electrostatic precipitation, Fuel Processing Technology, 2004, 85:781-798.)专利一种电除尘装置(201010607898.0)在电除尘器最后一级采用细密的金属丝网替代部分极线,实现荷电增强、惯性拦 截、布朗扩散捕捉、静电力强化、迁移距离缩短等多种作用。该技术可以增强除尘器其对细颗粒的捕获效率,但无法解决传统电除尘器清灰时二次扬尘的问题。综上,绝大部分改进对原有的电除尘器改动很大,难以推广。因此利用原有设备,提高电除尘捕集微小粒子的技术日益引起重视。  Aiming at the problem of low removal efficiency of PM 2.5 , the existing methods of improving the electrostatic precipitator mainly include optimizing the geometric parameters and operating parameters of the traditional electrostatic precipitator, adopting the principle of pre-coagulation to reunite the particles through bipolar charging, and adopting Mobile plates, wet electrostatic precipitators, etc. improve the cleaning process. The University of Ohio adopts a film-coated wet electrostatic precipitator, replacing stainless steel plates with fiber materials, and forming a water film on the surface of the plates, which can greatly reduce the use of steel and reduce secondary dust. (Membrane-based wet electrostatic precipitation, Fuel Processing Technology, 2004, 85:781-798.) A patented electrostatic precipitator (201010607898.0) uses a fine wire mesh to replace part of the pole line in the last stage of the electrostatic precipitator to realize the charge Electric enhancement, inertial interception, Brownian diffusion capture, electrostatic force enhancement, migration distance shortening and other functions. This technology can enhance the dust collector's capture efficiency of fine particles, but it cannot solve the problem of secondary dust generation when traditional electrostatic precipitators clean dust. To sum up, most of the improvements have made great changes to the original electrostatic precipitator and are difficult to popularize. Therefore, the use of existing equipment to improve the technology of electrostatic precipitator to capture tiny particles has attracted more and more attention.

发明内容 Contents of the invention

本专利针对传统电除尘设备捕获PM2.5效率不高、二次扬尘影响严重的问题,提供了一种干湿结合式静电除尘器及除尘方法。  This patent provides a dry-wet combined electrostatic precipitator and dust removal method for the problems of low efficiency of capturing PM 2.5 by traditional electrostatic precipitators and serious impact of secondary dust.

本发明所述的干湿结合式静电除尘器采用的技术方案为,采用现有的电除尘器,其内部包括多级电场,并对电场的后两级进行改造。所述除尘器的倒数第二级电场采用角钢长芒刺线、锯齿线或鱼骨型极线,增强倒数第二级电场对颗粒的荷电效果;除尘器的末级电场采用圆极线,增强末级电场的工作电压,形成强迁移电场,并减少电晕风对流场的影响;倒数第二级电场与末级电场的组合,提升了粒径在0.1-1μm的颗粒在末级电场的迁移速度和迁移率;在末级电场的极板上方设置若干个末级清灰喷水器,用水冲洗极板的方式取代振打清灰,确保附着在极板上的颗粒都可被清除,减小原来因振打导致的二次扬尘。  The technical solution adopted by the dry-wet combined electrostatic precipitator of the present invention is to adopt the existing electric precipitator, which includes multi-stage electric fields inside, and transform the last two stages of the electric field. The penultimate electric field of the dust collector adopts angle steel long burr wire, zigzag wire or herringbone pole line to enhance the charging effect of the penultimate electric field on the particles; the final electric field of the dust collector adopts a circular pole line, Enhance the working voltage of the final electric field, form a strong migration electric field, and reduce the influence of corona wind on the flow field; the combination of the penultimate electric field and the final electric field improves the particle size of 0.1-1μm in the final electric field The migration speed and mobility; set several last-stage ash cleaning sprinklers above the plate of the final electric field, and replace the vibration cleaning with water to wash the plate, so as to ensure that all the particles attached to the plate can be removed , to reduce the secondary dust caused by rapping. the

所述末级电场的极板采用耐腐蚀导电材料或镀覆耐腐蚀层,以避免湿式清灰带来的腐蚀问题。  The polar plate of the final electric field is made of corrosion-resistant conductive material or coated with a corrosion-resistant layer to avoid corrosion problems caused by wet cleaning. the

本发明所述的干湿结合式静电除尘方法,具体为:烟气进入除尘器,经过前几级电场,烟气中绝大部分颗粒已经被捕集;在最后两级电场中,烟气中颗粒以PM2.5居多,经过倒数第二级电场时,颗粒荷电会得到强化,并在末级的强迁移电场中运动至极板被捕获,提高除尘效率;清灰时,末级电场采用水清洗的方式,并通过调控末级清灰喷水器喷口的位置和流速,使喷出的水在极板表面形成水膜,大幅减少二次扬尘。  The dry-wet combined electrostatic precipitator method of the present invention is specifically as follows: the flue gas enters the dust collector, and most of the particles in the flue gas have been captured through the first few stages of electric fields; in the last two stages of electric fields, the flue gas Most of the particles are PM 2.5 . When they pass through the penultimate electric field, the charge of the particles will be strengthened, and they will move in the strong migration electric field of the final stage until the plate is captured, which improves the dust removal efficiency; when cleaning dust, the electric field of the final stage is cleaned with water. The way, and by adjusting the position and flow rate of the nozzle of the final dust cleaning sprinkler, the sprayed water forms a water film on the surface of the plate, which greatly reduces the secondary dust.

所述末级电场为适应湿式清灰的弱放电电场,减小电场击穿的概率和次数,保证除尘器稳定运行。  The final stage electric field is a weak discharge electric field suitable for wet dust cleaning, which reduces the probability and frequency of electric field breakdown and ensures the stable operation of the dust collector. the

所述末级电场的湿式清灰过程中,通过加入洗涤剂或辅以机械振打清灰方式以增强清灰效果。  In the wet cleaning process of the final electric field, the dust cleaning effect is enhanced by adding detergent or supplemented by mechanical vibration cleaning. the

本专利与现有技术相比的优势如下:  The advantages of this patent compared with the prior art are as follows:

(1)提高除尘效率,尤其是PM2.5的分级捕获效率。在最后两级电场根据其入口烟尘的特点,改变极线、极板的配置,实现前电场增强荷电、后电场增强迁移的组合,并在末电场通过湿式清灰引入热泳力、液桥力促进颗粒的迁移和粘附。已沉积在极板上的颗粒通过水冲可以最大限度的减少二次扬尘,从而在综合作用下大大提高除尘器对PM2.5的脱除效率;  (1) Improve dust removal efficiency, especially the graded capture efficiency of PM 2.5 . In the last two stages of electric field, according to the characteristics of the smoke and dust at the entrance, the configuration of the pole line and the plate is changed to realize the combination of enhanced charging by the front electric field and enhanced migration by the rear electric field, and introduce thermophoretic force and liquid bridge force through wet cleaning in the final electric field Facilitates migration and adhesion of particles. The particles that have been deposited on the plate can minimize the secondary dust through water flushing, thus greatly improving the removal efficiency of the dust collector for PM 2.5 under the comprehensive effect;

(2)末级电场的极线极板配置调控为适应湿式清灰的弱放电电场,减小电场击穿的概率和次数,保证除尘器稳定运行。而且通过控制水喷嘴的布置及清灰周期,保证极板的上不会覆盖较厚的灰层,减少灰层反电晕的影响,维持极线极板间的均匀强电场。  (2) The pole line plate configuration of the final electric field is adjusted to adapt to the weak discharge electric field of wet dust cleaning, reduce the probability and frequency of electric field breakdown, and ensure the stable operation of the dust collector. Moreover, by controlling the arrangement of the water nozzles and the cleaning cycle, it is ensured that the plates will not be covered with a thicker ash layer, reducing the impact of the back corona of the ash layer, and maintaining a uniform strong electric field between the polar plates. the

(3)应用前景好,成本低。对原有的传统电除尘器改动小,极线、极板的改造容易实现,且在最后一级使用湿式除尘,灰量少,耗水量少,清灰周期长。  (3) Good application prospect and low cost. The modification of the original traditional electrostatic precipitator is small, the transformation of the polar line and the polar plate is easy to realize, and the wet dust removal is used in the last stage, with less ash, less water consumption, and a long cleaning cycle. the

附图说明 Description of drawings

图1是改进后干湿结合式静电除尘器的整体结构示意图。  Figure 1 is a schematic diagram of the overall structure of the improved dry-wet combined electrostatic precipitator. the

图2(a)和图2(b)分别是干湿结合式静电除尘器倒数第二级电场和末级电场的结构示意图。  Figure 2(a) and Figure 2(b) are the structure diagrams of the penultimate electric field and the final electric field of the dry-wet combined electrostatic precipitator, respectively. the

图3是干湿结合式静电除尘器末级电场的局部结构示意图。  Figure 3 is a schematic diagram of the partial structure of the final stage electric field of the dry-wet combined electrostatic precipitator. the

图4是图3的正视图。  FIG. 4 is a front view of FIG. 3 . the

图中标号:  Labels in the figure:

1-除尘器烟气入口、2-倒数第二级电场、3-末级电场、4-除尘器出口、5-灰斗、6-倒数第二级电场极线、7-末级清灰喷水器、8-末级电场极线、9-极板。  1- Dust collector flue gas inlet, 2- penultimate electric field, 3- final electric field, 4- dust collector outlet, 5- ash hopper, 6- penultimate electric field pole line, 7- final dust cleaning spray Water container, 8-final electric field pole line, 9-polar plate. the

具体实施方式 Detailed ways

本发明提供了一种干湿结合式静电除尘器及除尘方法,下面结合附图和具体实施方式对本发明做进一步说明。  The present invention provides a dry-wet combined electrostatic precipitator and a dust removal method. The present invention will be further described below in conjunction with the accompanying drawings and specific implementation methods. the

传统静电除尘器中一般采用四电场的布置方式,经过前两级电场,大部分10μm以上的大颗粒都已经被极板捕获,烟气中残存的灰量为总灰量的10%以下,其中以粒径在2.5μm以下的细颗粒居多。  Traditional electrostatic precipitators generally adopt four electric field layouts. After the first two electric fields, most of the large particles over 10 μm have been captured by the plates, and the remaining ash in the flue gas is less than 10% of the total ash. Most of them are fine particles with a particle size below 2.5 μm. the

本发明所述的干湿结合式静电除尘器的整体结构如图1所示。该除尘器采用现有的电除尘器,包括除尘器烟气入口1、除尘器出口4、灰斗5及多个极板9,保留传统电除器前部电场的设计,从而实现对烟气中大粒径颗粒的脱除,并对电场的后两级进行改造。除尘器的倒数第二级电场2采用角钢长芒刺线、锯齿线或鱼骨型极线,增强倒数第二级电场对颗粒的荷电效果,如图2(a)所示;除尘器的末级电场3采用圆极线等放电效果较差、电场均匀的极线,增强末级电场的工作电压,形成强迁移电场,并减少电晕风对流场的影响;倒数第二级电场2与末级电场3的组合,提升了粒径在0.1-1μm的颗粒在末级电场的迁移速度和迁移率;在末级电场3的极板上方设置若干个末级清灰喷水器7,用水冲洗极板的方式取代振打清灰,确保附着在极板上的颗粒都可被清除,减小原来因振打导致的二次扬尘,如图2(b)、图3和图4所示;而且极板在冲洗后表面会附着一层温度较低的液膜,有利于通过热泳力、液桥力等使颗粒附着在极板上。末级电场3的极板采用耐腐蚀导电材料或镀覆耐腐蚀层,以避免湿式清灰带来的腐蚀问题,保证电除尘器正常工作。  The overall structure of the dry-wet combined electrostatic precipitator described in the present invention is shown in FIG. 1 . The dust collector adopts the existing electrostatic precipitator, including dust collector flue gas inlet 1, dust collector outlet 4, ash hopper 5 and multiple plates 9, and retains the design of the electric field at the front of the traditional electrostatic precipitator, so as to realize the control of flue gas The removal of medium and large particle size particles, and the transformation of the last two stages of the electric field. The penultimate electric field 2 of the dust collector adopts angle steel long burr wire, zigzag wire or herringbone pole line to enhance the charging effect of the penultimate electric field on the particles, as shown in Figure 2 (a); the dust collector The final electric field 3 adopts polar lines with poor discharge effect and uniform electric field, such as circular polar lines, to enhance the working voltage of the final electric field, form a strong migration electric field, and reduce the influence of corona wind on the flow field; the penultimate electric field 2 The combination with the final electric field 3 improves the migration speed and mobility of particles with a particle size of 0.1-1 μm in the final electric field; several final dust cleaning sprinklers 7 are set above the plate of the final electric field 3, The method of rinsing the plate with water instead of vibrating to remove dust can ensure that all the particles attached to the plate can be removed and reduce the secondary dust caused by rapping, as shown in Figure 2(b), Figure 3 and Figure 4 In addition, a layer of liquid film with a lower temperature will be attached to the surface of the plate after washing, which is conducive to making particles adhere to the plate through thermophoretic force and liquid bridge force. The plate of the final electric field 3 is made of corrosion-resistant conductive material or coated with a corrosion-resistant layer to avoid corrosion problems caused by wet cleaning and ensure the normal operation of the electrostatic precipitator. the

运行过程中,由于PM2.5在总灰量中的比重很小,因此末级清灰的周期很长,耗水量少。另外,末级圆极线形成的强电场更为均匀,可以减少末级湿式除尘器电场击穿的几率,保障其长期正常运行。实现干湿结合式静电除尘器的高效经济运行。最终被捕获的灰被收集在灰斗5,净化气体由除尘器出口4流出。  During the operation, since the proportion of PM 2.5 in the total ash is very small, the period of final cleaning is very long and the water consumption is small. In addition, the strong electric field formed by the final circular polar line is more uniform, which can reduce the probability of electric field breakdown of the final wet dust collector and ensure its long-term normal operation. Realize the efficient and economical operation of the dry-wet combined electrostatic precipitator. The finally captured ash is collected in the ash hopper 5, and the purified gas flows out from the outlet 4 of the dust collector.

正常工作过程中,其对PM2.5的主要捕获脱除机制为:  During normal work, its main capture and removal mechanism for PM 2.5 is:

(1)在倒数第二级电场中,通过改变极线、极板的配置,增强放电效果,提升空间中自由离子的浓度,使PM2.5更易被荷电,从而有利于在电场中捕获;  (1) In the penultimate electric field, by changing the configuration of polar lines and plates, the discharge effect is enhanced, the concentration of free ions in the space is increased, and PM 2.5 is more easily charged, which is beneficial to capture in the electric field;

(2)在末级电场中,将极线极板的配置变为利于形成均匀稳定的强迁移电场,弱化放电效果,减小电晕风造成的湍流所带来的扬尘,使颗粒易被捕获且不易逃逸;  (2) In the final electric field, the configuration of the polar plate is changed to facilitate the formation of a uniform and stable strong migration electric field, weaken the discharge effect, reduce the dust caused by the turbulence caused by the corona wind, and make the particles easy to be captured and not easy to escape;

(3)清灰过程中,末级电场的极板以水洗的方式可以避免振打极板,使沉积在极板上的灰斗可以被收集,从而大幅降低二次扬尘。并可以根据灰颗粒性质不同,在清洗液中添加洗涤剂,保证颗粒都可以被清除;  (3) During the cleaning process, the plate of the final electric field is washed with water to avoid rapping the plate, so that the ash bucket deposited on the plate can be collected, thereby greatly reducing the secondary dust. And according to the different properties of the dust particles, detergent can be added to the cleaning solution to ensure that the particles can be removed;

(4)末级电场选择的均匀低放电强迁移电场,可以减少湿烟气中的发生击穿现象的几率,保证除尘器稳定运行;  (4) The uniform low discharge and strong migration electric field selected by the final electric field can reduce the probability of breakdown in wet flue gas and ensure the stable operation of the dust collector;

(5)末级电场使用湿式清灰可以使绝大部分灰尘被清除,减少反电晕的发生,从而保证极线、极板间强电场的稳定;  (5) The use of wet dust cleaning in the final electric field can remove most of the dust and reduce the occurrence of back corona, thereby ensuring the stability of the strong electric field between the polar lines and the plates;

(6)末级电场中极板使用碳纤维等耐腐蚀的导电材料替代不锈钢,或在极板表面镀耐腐蚀层,提升极板的抗腐蚀性,保证正常运行;  (6) In the final electric field, carbon fiber and other corrosion-resistant conductive materials are used instead of stainless steel for the plates, or a corrosion-resistant layer is plated on the surface of the plates to improve the corrosion resistance of the plates and ensure normal operation;

(7)末级电场中,经水冲洗过的极板会在表面形成一层温度较低的水膜,烟气中的颗粒会在热泳力的作用下驱进板壁,并被流体液桥力附着在极板表面,增强捕获效果;  (7) In the final electric field, the electrode plate washed by water will form a layer of water film with a lower temperature on the surface, and the particles in the flue gas will be driven into the plate wall under the action of thermophoretic force, and will be driven into the plate wall by the fluid bridge force. Attached to the surface of the plate to enhance the capture effect;

其中,上述机制(1)和(2)根据末级电场入口烟尘的特点,增强了除尘器 在多场耦合作用下捕获PM2.5的能力,机制(3)通过湿式清灰确保已被捕获的颗粒不会发生二次扬尘现象,机制(4)、(5)和(6)使极线极板形式与湿式清灰方式相互配合,保证设备稳定高效运行,机制(7)引入热泳力促进颗粒向极板驱进运动,并在极板表面通过流体液桥力粘附在板壁,增强捕获效果。  Among them, the above mechanisms (1) and (2) enhance the ability of the dust collector to capture PM 2.5 under the action of multi-field coupling according to the characteristics of the dust at the entrance of the final electric field, and the mechanism (3) ensures that the captured particles There will be no secondary dusting phenomenon. Mechanisms (4), (5) and (6) make the polar plate form cooperate with the wet dust cleaning method to ensure stable and efficient operation of the equipment. Mechanism (7) introduces thermophoretic force to promote particles to The polar plate is driven into motion, and adheres to the plate wall through the fluid liquid bridge force on the surface of the polar plate to enhance the capture effect.

Claims (5)

1. do wet convolution electrostatic precipitator for one kind, inside comprises multistage electric field, it is characterized in that, the penultimate stage electric field of described deduster adopts the long prickle wire of angle steel, jaggies or fish bone well polar curve, strengthens the penultimate stage electric field to the charged effect of particle; The final stage electric field of deduster adopts the entelechy line, strengthens the operating voltage of final stage electric field, forms strong migration electric field, and reduces the impact of corona wind stream field; The combination of penultimate stage electric field and final stage electric field has promoted particle diameter in the particle of 0.1-1 μ m migration velocity and the mobility at the final stage electric field; Several final stage deashing water jets are set above the pole plate of final stage electric field, and the mode that water rinses pole plate replaces vibration dust-cleaning, and the particle of guaranteeing to be attached on pole plate all can be eliminated, and reduces the reentrainment of dust that originally caused because of rapping.
2. a kind of wet convolution electrostatic precipitator of doing according to claim 1, is characterized in that, the pole plate of described final stage electric field adopts anti-corrosion electric conducting material or plating anti-corrosion layer, with the etching problem of avoiding the wet type deashing to bring.
3. the convolution electrostatic dust removing method that wets of doing based on deduster claimed in claim 1, is characterized in that, flue gas enters deduster, and through front what electric field, in flue gas, most particles are captured; In the end in the two-stage electric field, in flue gas, particle is with PM 2.5In the majority, during through the penultimate stage electric field, charging particle can be strengthened, and moves to pole plate be hunted down in the strong migration electric field of final stage, improves efficiency of dust collection; During deashing, the mode that the final stage electric field adopts water to clean, and by regulating and controlling position and the flow velocity of final stage deashing water jet spout, make the water of ejection form moisture film at polar board surface, significantly reduce reentrainment of dust.
4. a kind of wet convolution electrostatic dust removing method of doing according to claim 3, it is characterized in that: described final stage electric field reduces probability and the number of times of electric field breakdown for adapting to the weak discharge electric field of wet type deashing, guarantees deduster stable operation.
5. a kind of wet convolution electrostatic dust removing method of doing according to claim 3, is characterized in that: in the wet type deashing process of described final stage electric field, by adding washing agent or being aided with the mechanical rapping cleaning dust mode to strengthen ash-removal effect.
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CN104722401A (en) * 2015-01-09 2015-06-24 李连清 Vehicle-mounted haze eliminator
CN105689132A (en) * 2016-03-11 2016-06-22 浙江信雅达环保工程有限公司 Dry-wet compound electric dust remover
CN107743420A (en) * 2015-06-29 2018-02-27 韩国电力公社 Flyash separates and retracting device
CN109647117A (en) * 2019-02-26 2019-04-19 北京合壹北科环保科技有限公司 A kind of flue gas refined dedusting device with dehydrating function

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Publication number Priority date Publication date Assignee Title
CN104190540A (en) * 2014-08-15 2014-12-10 浙江诸暨利达环保设备有限公司 Dry-wet mixed electric precipitation device
CN104722401A (en) * 2015-01-09 2015-06-24 李连清 Vehicle-mounted haze eliminator
CN107743420A (en) * 2015-06-29 2018-02-27 韩国电力公社 Flyash separates and retracting device
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CN109647117A (en) * 2019-02-26 2019-04-19 北京合壹北科环保科技有限公司 A kind of flue gas refined dedusting device with dehydrating function

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