[go: up one dir, main page]

CN104963746A - A device for collecting and processing smog particles - Google Patents

A device for collecting and processing smog particles Download PDF

Info

Publication number
CN104963746A
CN104963746A CN201510291216.2A CN201510291216A CN104963746A CN 104963746 A CN104963746 A CN 104963746A CN 201510291216 A CN201510291216 A CN 201510291216A CN 104963746 A CN104963746 A CN 104963746A
Authority
CN
China
Prior art keywords
assembly
particle
air
valve
particle catcher
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.)
Granted
Application number
CN201510291216.2A
Other languages
Chinese (zh)
Other versions
CN104963746B (en
Inventor
王铁
卜玉帅
高金瑞
张昕
蔡玲
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.)
Shenyang Ligong University
Original Assignee
Shenyang Ligong University
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 Shenyang Ligong University filed Critical Shenyang Ligong University
Priority to CN201510291216.2A priority Critical patent/CN104963746B/en
Publication of CN104963746A publication Critical patent/CN104963746A/en
Application granted granted Critical
Publication of CN104963746B publication Critical patent/CN104963746B/en
Expired - Fee Related legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Landscapes

  • Processes For Solid Components From Exhaust (AREA)
  • Electrostatic Separation (AREA)

Abstract

The invention aims to provide a haze particle treatment device, which not only can effectively collect and treat fine particles in exhaust gas, but also can directly receive and treat PM2.5 (fine particles with the particle size of less than or equal to 2.5 microns) which is already existed in large quantity in the atmosphere. The air containing haze particles is pumped into the haze particle collecting and processing device by the power device through the air inlet of the device for purification, and the air flowing out of the air outlet of the device is the air meeting the national standard. The device has strong universality, and can be applied to exhaust gas discharge outlets of equipment such as diesel engines and the like in the industrial field. When the method is applied to industrial production, the contents of particulate matters and soot in waste gas can be greatly reduced, and secondary dust pollution cannot be caused. The particle collecting and processing method is applied to the diesel vehicle, the particle collecting and processing efficiency is greatly improved compared with that of the traditional method, and the diesel vehicle exhaust has the advantages of small exhaust back pressure, pressure reduction, high particle collecting efficiency, complete particle post-processing and the like.

Description

一种雾霾颗粒收集处理装置A device for collecting and processing smog particles

技术领域 technical field

本发明属于空气净化技术领域,特别是涉及一种雾霾颗粒收集处理装置。 The invention belongs to the technical field of air purification, in particular to a device for collecting and treating haze particles.

背景技术 Background technique

近些年来,“雾霾”成了我们讨论的热点问题,并受到国家和人们的重视。而PM2.5(直径小于等于2.5微米的细颗粒物)被认为是造成雾霾天气的主要原因。现如今国家已将细颗粒物(PM2.5)浓度添加到空气质量指数指标中,空气中细颗粒物浓度成为了评定空气质量好坏的指标之一,国家的排放法规也变得日益严格。PM2.5在大气中的含量虽然不多,但与较粗大的颗粒物相比,PM2.5的粒径小,并且富含有大量的有害物质,且其在空气中的停留的时间长、输送的距离远,因而对人体健康和环境的影响更大。工业锅炉以及在工业生产过程中排放的烟尘、粉尘等是城市工业区大气污染的重要来源,如今工业中常用的除尘方法是旋风除尘和静电除尘。旋风除尘器,在气体流速较高时,其除尘效率较高,而当气体流速低时,由于颗粒物受到的离心力不足,造成颗粒的收集效率很低,并且其对细微粒的去除效果甚微。而如今在工业上广泛应用的静电除尘器,对于10微米以上的颗粒能达到99.9%的除尘效果,但是对PM2.5的除尘效率并不高,并且在气体流速大的情况下,由于电场作用于颗粒上的时间变短,其除尘效率会有明显的下降。 In recent years, "smog" has become a hot topic in our discussion, and has been valued by the country and people. PM2.5 (fine particulate matter with a diameter less than or equal to 2.5 microns) is considered to be the main cause of haze weather. Nowadays, the country has added the concentration of fine particulate matter (PM2.5) to the air quality index index. The concentration of fine particulate matter in the air has become one of the indicators for evaluating air quality, and the national emission regulations have become increasingly stringent. Although the content of PM2.5 in the atmosphere is not much, compared with coarser particles, PM2.5 has a small particle size and is rich in a large amount of harmful substances, and it stays in the air for a long time and transports The distance is far, so the impact on human health and the environment is greater. Industrial boilers and the smoke and dust emitted during industrial production are important sources of air pollution in urban industrial areas. Nowadays, the commonly used dust removal methods in industry are cyclone dust removal and electrostatic dust removal. The cyclone dust collector has a high dust removal efficiency when the gas flow rate is high, but when the gas flow rate is low, the particle collection efficiency is very low due to insufficient centrifugal force on the particles, and its removal effect on fine particles is minimal. Nowadays, the electrostatic precipitator widely used in industry can achieve 99.9% dust removal effect for particles above 10 microns, but the dust removal efficiency for PM2.5 is not high. The time on the particles becomes shorter, and the dust removal efficiency will drop significantly.

随着工业发展和汽车保有量连年增加,汽车尾气和工业废气成为大气中PM2.5的主要来源,比如柴油车,其颗粒和炭烟的排放要比汽油机大几十倍甚至更多,柴油机颗粒排放已成为大气污染物的重要来源,也是造成雾霾天气的主要原因。然而现如今应用在汽车上的颗粒捕捉器,虽然颗粒的捕捉效率已经可以达到很高,有些甚至可以达到90%,然而其存在进气阻力大,压降大,在使用一段时间后,由于颗粒物的积累,造成排气背压变大,由此造成发动机动力性变坏,燃油经济性变差,颗粒捕捉效率变差等问题。而常规的除尘技术在处理现有工业设备所产生的废气和烟尘中如PM2.5等粒径较小的颗粒时,其效率低、可行性差,难以满足日益严格的排放法规的要求。 With the development of industry and the increase of car ownership year after year, automobile exhaust and industrial waste gas have become the main sources of PM2.5 in the atmosphere, such as diesel vehicles, whose emissions of particles and soot are dozens of times or more than those of gasoline engines, diesel engine particles Emissions have become an important source of air pollutants and the main cause of smog. However, the particle traps used in automobiles today, although the particle capture efficiency can reach very high, some can even reach 90%, but they have large air intake resistance and large pressure drop. After a period of use, due to the particle The accumulation of exhaust gas will cause the exhaust back pressure to increase, which will lead to poor engine power, poor fuel economy, and poor particle capture efficiency. However, conventional dust removal technology has low efficiency and poor feasibility when dealing with small particles such as PM2.5 in the exhaust gas and smoke generated by existing industrial equipment, and it is difficult to meet the requirements of increasingly stringent emission regulations.

发明内容 Contents of the invention

本发明目的是为了克服现有技术存在的缺陷,提供一种颗粒收集效率高,集颗粒凝聚、颗粒收集与颗粒处理于一体的一种新型的雾霾颗粒收集处理装置。 The purpose of the present invention is to overcome the defects of the prior art, and provide a new type of haze particle collection and treatment device which has high particle collection efficiency and integrates particle agglomeration, particle collection and particle treatment.

本发明所采用的技术解决方案是一种雾霾颗粒收集处理装置,包括装置进气口、电荷区总成、凝聚器、静电旋风颗粒捕捉器总成、电磁颗粒捕捉器总成和装置出气口,所述的装置进气口与电荷区总成相连接,所述的电荷区总成与静电旋风颗粒捕捉器总成之间设置有凝聚器,所述的静电旋风颗粒捕捉器总成与电磁颗粒捕捉器总成相连接,所述的电磁颗粒捕捉器总成的一端设置有装置出气口。 The technical solution adopted in the present invention is a haze particle collection and treatment device, including the device air inlet, charge area assembly, agglomerator, electrostatic cyclone particle catcher assembly, electromagnetic particle catcher assembly and device air outlet , the air inlet of the device is connected to the charge area assembly, and an agglomerator is arranged between the charge area assembly and the electrostatic cyclone particle catcher assembly, and the electrostatic cyclone particle catcher assembly is connected to the electromagnetic The particle catcher assembly is connected, and one end of the electromagnetic particle catcher assembly is provided with an air outlet of the device.

还包括电子控制单元、空气流量计和第一空气阀,所述的空气流量计设置在装置进气口,所述的空气流量计的信号出端与电子控制单元的信号输入端相连接。 It also includes an electronic control unit, an air flow meter and a first air valve, the air flow meter is arranged at the air inlet of the device, and the signal output end of the air flow meter is connected to the signal input end of the electronic control unit.

所述的电荷区总成包括正极金属网、负极金属网、绝缘板和外壳,所述的绝缘板设置在外壳中间,将电荷区分隔成两部分,每部分内均匀设置有金属网,被分隔开的金属网与正电极相连接的为正极金属网与负电极相连接的为负极金属网。 The charge area assembly includes a positive metal mesh, a negative metal mesh, an insulating plate and a casing, the insulating plate is arranged in the middle of the casing, and separates the charge area into two parts, and each part is evenly provided with a metal mesh, which is divided into two parts. The separated metal mesh is connected with the positive electrode as the positive electrode metal mesh and the one connected with the negative electrode is the negative electrode metal mesh.

所述的凝聚器的壳体内设置有由叶轮叶片和叶轮轴组成的叶轮,所述的凝聚器和静电旋风颗粒捕捉器总成之间设置有第一空气阀。所述的第一空气阀的信号出端与电子控制单元的信号入端相连接。 The casing of the agglomerator is provided with an impeller composed of impeller blades and an impeller shaft, and a first air valve is arranged between the agglomerator and the electrostatic cyclone particle catcher assembly. The signal output port of the first air valve is connected with the signal input port of the electronic control unit.

所述的静电旋风颗粒捕捉器总成包括静电旋风颗粒捕捉器总成进气口、外筒、内筒、颗粒收集器、静电旋风颗粒捕捉器总成出气口、芒刺电极和中心柱,所述的静电旋风颗粒捕捉器总成进气口与凝聚器出气口相连接,所述的内筒设置在外筒内一端与静电旋风颗粒捕捉器总成出气口相连接,所述的外筒内设置有中心柱,所述的中心柱的表面均匀设置有芒刺电极,所述的外筒底部设置有颗粒收集器。 The electrostatic cyclone particle catcher assembly includes an electrostatic cyclone particle catcher assembly air inlet, an outer cylinder, an inner cylinder, a particle collector, an electrostatic cyclone particle catcher assembly air outlet, a prickly electrode and a central column. The air inlet of the electrostatic cyclone particle catcher assembly is connected to the air outlet of the coalescer, the inner cylinder is arranged in the outer cylinder and one end is connected to the air outlet of the electrostatic cyclone particle catcher assembly, and the outer cylinder is set There is a central column, the surface of the central column is uniformly provided with thorn electrodes, and the bottom of the outer cylinder is provided with a particle collector.

所述的电磁颗粒捕捉器总成分为正电荷区、磁场区、负电荷区和加热区,包括电磁颗粒捕捉器总成进气口、第二空气阀、正电荷区外壳、正电荷区电极、加热区外壳、负电荷区电极、阀门、电磁颗粒捕捉器总成出气口、电热丝、上下收集板、旁通阀、匀强磁场和旁通道,所述的电磁颗粒捕捉器总成进气口与静电旋风颗粒捕捉器总成出气口相连接,所述的电磁颗粒捕捉器总成进气口设置有旁通道和二次空气入口,所述的二次空气入口内设置有第二空气阀,所述的旁通道另一端与电磁颗粒捕捉器总成出气口相连接,所述的电磁颗粒捕捉器总成进气口与正电荷区外壳相连接,所述的正电荷区电极均匀分布在正电荷区外壳内,所述的上下收集板之间设置有匀强磁场和负电荷区电极,所述的上下收集板外为加热区,内设置有电热丝,所述的电磁颗粒捕捉器总成出气口处设置有阀门,所述的旁通道内设置有旁通阀。 The overall composition of the electromagnetic particle catcher includes a positive charge area, a magnetic field area, a negative charge area and a heating area, including an air inlet of the electromagnetic particle catcher assembly, a second air valve, a shell of the positive charge area, an electrode of the positive charge area, The shell of the heating zone, the electrode in the negative charge zone, the valve, the air outlet of the electromagnetic particle catcher assembly, the heating wire, the upper and lower collecting plates, the bypass valve, the uniform magnetic field and the bypass channel, and the air inlet of the electromagnetic particle catcher assembly It is connected with the air outlet of the electrostatic cyclone particle catcher assembly, the air inlet of the electromagnetic particle catcher assembly is provided with a bypass channel and a secondary air inlet, and a second air valve is arranged in the secondary air inlet, The other end of the bypass channel is connected to the air outlet of the electromagnetic particle catcher assembly, the air inlet of the electromagnetic particle catcher assembly is connected to the shell of the positive charge area, and the electrodes of the positive charge area are evenly distributed in the positive charge area. In the shell of the charge zone, a uniform magnetic field and a negative charge zone electrode are arranged between the upper and lower collecting plates, the outside of the upper and lower collecting plates is a heating zone, and a heating wire is arranged inside, and the electromagnetic particle catcher assembly A valve is arranged at the air outlet, and a bypass valve is arranged in the bypass channel.

所述的叶轮、旁通阀、阀门、第一空气阀和第二空气阀的信号输入端与电子控制单元的信号输出端相连接。 The signal input ends of the impeller, the bypass valve, the valve, the first air valve and the second air valve are connected with the signal output end of the electronic control unit.

所述的电荷区总成外壳、凝聚器外壳、叶轮叶片和正电荷区外壳采用绝缘材料制成。 The shell of the charge zone assembly, the shell of the condenser, the impeller blades and the shell of the positive charge zone are made of insulating materials.

与现有技术相比,本发明所具有的有益效果为:使颗粒的收集效率大大提高,弥补了传统除尘器的缺陷,不仅可以用来有效去除工业废中的颗粒和烟尘,有效的降低柴油机PM2.5的排放,使颗粒物浓度降低到环保排放要求,还可以对现存于大气中的雾霾颗粒进行收集处理,净化我们的空气,改善我们的空气质量和生活环境。具有很高的实用价值和应用前景,具有集颗粒凝聚、颗粒收集与颗粒处理于一体的优点。应用于柴油机上,可以使柴油机在排气过程中具有排气背压小,压降低,颗粒收集效率高,颗粒后处理完全等优点,使其可以满足日益严格的排放法规的要求。应用在产生废气的工业设备废气排放出口处,该雾霾颗粒收集处理装置可以大幅减少PM2.5的排放,从而改善我们的空气质量和生存环境。 Compared with the prior art, the present invention has the beneficial effects of greatly improving the collection efficiency of particles, making up for the defects of traditional dust collectors, not only being able to effectively remove particles and soot in industrial waste, but also effectively reducing diesel engine dust. The emission of PM2.5 reduces the concentration of particulate matter to the emission requirements of environmental protection. It can also collect and process the smog particles existing in the atmosphere, purify our air, and improve our air quality and living environment. It has high practical value and application prospect, and has the advantages of integrating particle coagulation, particle collection and particle treatment. Applied to the diesel engine, the diesel engine can have the advantages of small exhaust back pressure, low pressure drop, high particle collection efficiency and complete particle post-treatment during the exhaust process, so that it can meet the requirements of increasingly stringent emission regulations. Applied at the exhaust outlet of industrial equipment that produces exhaust gas, the haze particle collection and treatment device can greatly reduce PM2.5 emissions, thereby improving our air quality and living environment.

附图说明     Description of drawings

图1是本发明总的结构示意图; Fig. 1 is a general structural representation of the present invention;

图2是为本发明的电荷区总成示意图; Fig. 2 is a schematic diagram of the charge area assembly of the present invention;

图3是为本发明的电荷区总成AA剖视图; FIG. 3 is a sectional view of the charge region assembly AA of the present invention;

    图4为本发明的静电旋风颗粒捕捉器总成示意图; Figure 4 is a schematic diagram of the electrostatic cyclone particle catcher assembly of the present invention;

图5为本发明的电磁颗粒捕捉器总成示意图; Fig. 5 is the schematic diagram of the electromagnetic particle catcher assembly of the present invention;

图6为叶轮示意图; Figure 6 is a schematic diagram of the impeller;

图7为叶轮侧视图。 Figure 7 is a side view of the impeller.

图中: In the picture:

1-装置进气口 2-空气流量计 3电荷区总成 4-凝聚器 5-第一空气阀 1-Device air inlet 2-Air flow meter 3Charge area assembly 4-Aggregator 5-First air valve

6-静电旋风颗粒捕捉器总成 7-电磁颗粒捕捉器总成 8-装置出气口 6-Electrostatic cyclone particle catcher assembly 7-Electromagnetic particle catcher assembly 8-Device outlet

9-正极金属网 10-负极金属网 11-绝缘板 12-外壳 13-静电旋风颗粒捕捉器总成进气口  14-外筒  15-内筒  16-颗粒收集器17-静电旋风颗粒捕捉器总成出气口  18-芒刺电极  19-中心柱 20-电磁颗粒捕捉器总成进气口 9-Positive metal mesh 10-Negative metal mesh 11-Insulation plate 12-Shell 13-Inlet of electrostatic cyclone particle catcher assembly 14-Outer cylinder 15-Inner cylinder 16-Particle collector 17-Electrostatic cyclone particle catcher assembly Air outlet 18-Prickly electrode 19-Central column 20-Inlet of electromagnetic particle catcher assembly

21-第二空气阀  22-正电荷区外壳  23-正电荷区电极 24-正电荷区  25-加热区外壳 26-加热区  27-负电荷区电极  28-阀门 29-电磁颗粒捕捉器总成出气口 30-电热丝  31-负电荷区  32-磁场区 33-上下收集板  34-旁通阀  35-匀强磁场  36-旁通道 37-叶轮叶片  38-叶轮轴  39-电子控制单元。 21-Second air valve 22-Positive charge area shell 23-Positive charge area electrode 24-Positive charge area 25-Heating area shell 26-Heating area 27-Negative charge area electrode 28-Valve 29-Electromagnetic particle catcher assembly out Gas port 30-heating wire 31-negative charge area 32-magnetic field area 33-upper and lower collecting plate 34-bypass valve 35-uniform magnetic field 36-bypass channel 37-impeller blade 38-impeller shaft 39-electronic control unit.

具体实施方式 Detailed ways

实施例1: Example 1:

如图1所示,一种雾霾颗粒收集处理装置,包括装置进气口1、电荷区总成3、凝聚器4、静电旋风颗粒捕捉器总成6、电磁颗粒捕捉器总成7和装置出气口8和与装置进气口1相连接的抽风装置,所述的进气口与电荷区总成3相连接,所述的电荷区总成3与静电旋风颗粒捕捉器总成6之间设置有凝聚器4,所述的静电旋风颗粒捕捉器总成6与电磁颗粒捕捉器总成7相连接,所述的电磁颗粒捕捉器总成7的一端设置有装置出气口8。 As shown in Figure 1, a kind of smog particle collection treatment device, comprises device air inlet 1, charge area assembly 3, agglomerator 4, electrostatic cyclone particle catcher assembly 6, electromagnetic particle catcher assembly 7 and device The air outlet 8 and the draft device connected with the air inlet 1 of the device, the air inlet is connected with the charge area assembly 3, between the charge area assembly 3 and the electrostatic cyclone particle catcher assembly 6 An agglomerator 4 is provided, the electrostatic cyclone particle catcher assembly 6 is connected with an electromagnetic particle catcher assembly 7 , and an air outlet 8 is provided at one end of the electromagnetic particle catcher assembly 7 .

还包括电子控制单元39和空气流量计2,电子控制单元39,选用Xilinx公司的Virtex系列的FPGA控制单元。所述的空气流量计2设置在装置进气口1,所述的空气流量计2的信号出端与电子控制单元39的信号输入端相连接。空气流量计2用来准确的监测流入颗粒处理装置的气体,并将气体的进气量、进气密度、进气温度信号传输给电子控制单元39。 It also includes an electronic control unit 39 and an air flow meter 2, and the electronic control unit 39 is an FPGA control unit of the Virtex series of Xilinx Company. The air flow meter 2 is arranged at the air inlet 1 of the device, and the signal output end of the air flow meter 2 is connected with the signal input end of the electronic control unit 39 . The air flow meter 2 is used to accurately monitor the gas flowing into the particle processing device, and transmit the gas intake volume, intake density, and intake temperature signals to the electronic control unit 39 .

如图2和图3所示:所述的电荷区总成3包括正极金属网9、负极金属网10、绝缘板11和外壳12,所述的绝缘板11设置在外壳中间,将电荷区分隔成两部分,每部分内均匀设置有金属网,被分隔开的金属网与正电极相连接的为正极金属网9,使其带高压正电;与负电极相连接的为负极金属网10,使其带高压负电。这样做的目的是为了使含有颗粒的气体经过电荷区,使其中的颗粒分别带上正负电荷。 As shown in Figure 2 and Figure 3: the charge area assembly 3 includes a positive electrode metal mesh 9, a negative electrode metal mesh 10, an insulating plate 11 and a casing 12, and the insulating plate 11 is arranged in the middle of the casing to separate the charge area It is divided into two parts, and each part is evenly equipped with a metal mesh. The separated metal mesh is connected to the positive electrode as the positive electrode metal mesh 9, so that it is charged with high voltage positive electricity; the one connected to the negative electrode is the negative electrode metal mesh 10. , making it negatively charged at high voltage. The purpose of doing this is to make the gas containing particles pass through the charge zone, so that the particles in it are respectively positively and negatively charged.

如图6和图7所示:所述的凝聚器4的壳体内设置有由叶轮叶片37和叶轮轴38组成的叶轮,所述的凝聚器4和静电旋风颗粒捕捉器总成6之间设置有第一空气阀5。在凝聚器4内部带异种电荷的颗粒可以充分混合并发生凝聚,从而使颗粒的粒径变大。以便于后面的颗粒的收集和处理。 As shown in Figures 6 and 7: the housing of the agglomerator 4 is provided with an impeller consisting of impeller blades 37 and an impeller shaft 38, and the agglomerator 4 and the electrostatic cyclone particle catcher assembly 6 are arranged There is a first air valve 5 . Particles with different charges in the agglomerator 4 can be fully mixed and agglomerated, so that the particle size of the particles becomes larger. In order to facilitate the subsequent collection and processing of particles.

如图4所示:所述的静电旋风颗粒捕捉器总成6包括静电旋风颗粒捕捉器总成进气口13、外筒14、内筒15、颗粒收集器16、静电旋风颗粒捕捉器总成出气口17、芒刺电极18和中心柱19,所述的电旋风颗粒捕捉器总成进气口与凝聚器4出气口相连接,所述的内筒15设置在外筒14内一端与静电旋风颗粒捕捉器总成出气口17相连接,所述的外筒14内设置有中心柱19,所述的中心柱19的表面均匀设置有芒刺电极18,所述的外筒14底部设置有颗粒收集器16。气流由上边的静电旋风颗粒捕捉器总成进气口13切向流入,中心柱19接高压电源,外筒14接地。气体由下部静电旋风颗粒捕捉器总成出气口17排出。 As shown in Figure 4: the electrostatic cyclone particle catcher assembly 6 includes an electrostatic cyclone particle catcher assembly air inlet 13, an outer cylinder 14, an inner cylinder 15, a particle collector 16, and an electrostatic cyclone particle catcher assembly Air outlet 17, prickly electrode 18 and central column 19, the air inlet of the electric cyclone particle catcher assembly is connected with the air outlet of the coagulator 4, and the inner cylinder 15 is arranged at one end of the outer cylinder 14 to connect with the electrostatic cyclone The air outlet 17 of the particle catcher assembly is connected, and the outer cylinder 14 is provided with a central column 19, and the surface of the central column 19 is uniformly provided with prickly electrodes 18, and the bottom of the outer cylinder 14 is provided with particles Collector 16. The air flow flows in tangentially from the air inlet 13 of the electrostatic cyclone particle catcher assembly on the top, the central column 19 is connected to a high-voltage power supply, and the outer cylinder 14 is grounded. The gas is discharged from the gas outlet 17 of the lower electrostatic cyclone particle catcher assembly.

如图5所示:所述的电磁颗粒捕捉器总成7分为正电荷区24、磁场区32、负电荷区31和加热区26,包括电磁颗粒捕捉器总成进气口20、第二空气阀21、正电荷区外壳22、正电荷区电极23、加热区外壳25、负电荷区电极27、阀门、电磁颗粒捕捉器总成出气口29、电热丝30、上下收集板33、旁通阀34、匀强磁场35和旁通道36,所述的电磁颗粒捕捉器总成进气口20与静电旋风颗粒捕捉器总成出气口17相连接,所述的电磁颗粒捕捉器总成进气口20设置有旁通道36和二次空气入口,所述的二次空气入口内设置有第二空气阀21,所述的旁通道36另一端与电磁颗粒捕捉器总成出气口29相连接,所述的电磁颗粒捕捉器总成进气口20与正电荷区外壳22相连接,所述的正电荷区电极23均匀分布在正电荷区外壳22内,正电荷区电极23接有10-105kv的高压正电,所述的上下收集板33之间设置有匀强磁场35和负电荷区电极27,磁场区32具体为若干线圈产生的匀强磁场35构成,上半部分磁场方向垂直纸面向外,下半部分垂直纸面向里。负电荷区装有若干个接有10-105kv的高压负电的负电荷区电极27;所述的上下收集板33外为加热区26,设置有电热丝30,目的是接收来自电子控制单元39的信号,给负电荷区和磁场区32进行加热,对吸附的颗粒进行颗粒的加热处理,将吸附在负电荷区域和磁场区32域的颗粒燃烧掉,防止背压变得过大;所述的电磁颗粒捕捉器总成出气口29设置有阀门,所述的旁通道36内设置有旁通阀34,旁通阀34平时是关闭的,目的是在对吸附的颗粒进行颗粒燃烧处理时,关闭阀门,打开旁通阀34,使经过一次颗粒处理后的气体从旁通道36经过旁通阀34流走,以便于对负电荷区31和磁场区32吸附的颗粒进行燃烧;所述的二次空气入口中装有第二空气阀21目的是当电热丝30开始加热时,第二空气阀平时是关闭的,第二空气阀打开供给一定量的二次空气。 As shown in Figure 5: described electromagnetic particle catcher assembly 7 is divided into positive charge area 24, magnetic field area 32, negative charge area 31 and heating area 26, comprises electromagnetic particle catcher assembly air inlet 20, the second Air valve 21, positive charge area shell 22, positive charge area electrode 23, heating area shell 25, negative charge area electrode 27, valve, electromagnetic particle catcher assembly air outlet 29, heating wire 30, upper and lower collecting plates 33, bypass Valve 34, uniform magnetic field 35 and bypass channel 36, the air inlet 20 of the electromagnetic particle catcher assembly is connected with the air outlet 17 of the electrostatic cyclone particle catcher assembly, the air intake of the electromagnetic particle catcher assembly The port 20 is provided with a bypass channel 36 and a secondary air inlet, the secondary air inlet is provided with a second air valve 21, and the other end of the bypass channel 36 is connected to the air outlet 29 of the electromagnetic particle catcher assembly, The air inlet 20 of the electromagnetic particle catcher assembly is connected to the shell 22 of the positive charge area, and the electrodes 23 of the positive charge area are evenly distributed in the shell 22 of the positive charge area, and the electrodes 23 of the positive charge area are connected with 10-105kv The high-voltage positive electricity, the upper and lower collecting plates 33 are provided with a uniform magnetic field 35 and a negative charge region electrode 27, the magnetic field region 32 is specifically composed of a uniform magnetic field 35 generated by a number of coils, and the direction of the upper half of the magnetic field is perpendicular to the surface of the paper. Outside, the lower half of the vertical paper faces inward. The negative charge area is equipped with several negative charge area electrodes 27 connected with high-voltage negative electricity of 10-105kv; Signal, heating the negative charge area and the magnetic field area 32, heat the adsorbed particles, burn the particles adsorbed in the negative charge area and the magnetic field area 32, and prevent the back pressure from becoming too large; The air outlet 29 of the electromagnetic particle catcher assembly is provided with a valve, and the bypass channel 36 is provided with a bypass valve 34, which is normally closed for the purpose of closing the adsorbed particles during the particle combustion process. Valve, open the bypass valve 34, so that the gas after the primary particle treatment flows away from the bypass channel 36 through the bypass valve 34, so as to burn the particles adsorbed by the negative charge area 31 and the magnetic field area 32; The second air valve 21 purpose is housed in the air inlet is that when the heating wire 30 starts to heat, the second air valve is closed at ordinary times, and the second air valve is opened to supply a certain amount of secondary air.

所述的叶轮、旁通阀34、阀门、第一空气阀5和第二空气阀21的信号输入端与电子控制单元39的信号输出端相连接。电子控制单元39经过判断空气流量计2输入的信息控制第一空气阀5的开度,从而控制气体的流速。 The signal input ends of the impeller, the bypass valve 34 , the valves, the first air valve 5 and the second air valve 21 are connected with the signal output end of the electronic control unit 39 . The electronic control unit 39 controls the opening degree of the first air valve 5 by judging the information input by the air flow meter 2 , so as to control the flow rate of the gas.

所述的电荷区总成外壳、凝聚器外壳、叶轮叶片37和正电荷区外壳采用绝缘材料制成。本领域熟练技术人员可根据现有技术进行选择。 The shell of the charge zone assembly, the shell of the condenser, the impeller blades 37 and the shell of the positive charge zone are made of insulating materials. Those skilled in the art can select according to the prior art.

工作过程:气体由装置进气口1进入该雾霾颗粒收集处理装置,在电荷区总成3内,含有颗粒的气体分别流过带有高压正电的正极金属网9和带高压负电的负极金属网10,从而使气体中的颗粒分别带上正电荷和负电荷。正极金属网9和负极金属网10之间用绝缘板隔开。分别带有正电荷和负电荷的气体流入凝聚器4中,气体冲击叶轮的叶片使叶轮转动,使带有不同电荷的颗粒充分混合并发生凝聚,从而使气体中的颗粒的粒径变大,实现颗粒的生长,以便于后续颗粒的收集与处理。含有粒径变大的颗粒的气体切向流入静电旋风颗粒捕捉器总成6,气体在静电旋风颗粒捕捉器总内的运动示意图如图4所示,气体中的颗粒在离心力和静电场力的作用下被甩到了外筒14的内壁上,并且在重力的作用下滑落到颗粒收集器16中。另外,本静电旋风颗粒捕捉总成仍具有传统的旋风除尘器的优点,具有自动清灰功能,并且不会产生二次扬尘。最后经过一次颗粒捕捉的气体由静电旋风微粒捕捉器总成出气口流出,流入电磁颗粒捕捉器总成7。气体中未被有效去除的颗粒经过正电荷区电极23而带正电,而后带有正电荷的颗粒进入匀强磁场35,在洛仑磁力和库仑力的共同作用下发生偏转,分别偏向上下收集板。而后仍然残剩下来的带有正电荷的颗粒进入负电荷区31,吸附在负电荷区31内,最后满足排放要求的气体由电磁颗粒捕捉器总成出气口29排出该雾霾颗粒收集处理装置。所述对电极和电磁线圈的选择和设置为本领域的现有技术,本领域熟练技术人员可根据现有技术进行选择和设置。 Working process: gas enters the smog particle collection and treatment device from the device air inlet 1, and in the charge area assembly 3, the gas containing particles flows through the positive metal mesh 9 with high voltage positive charge and the negative electrode with high voltage negative charge respectively The metal mesh 10, so that the particles in the gas are respectively positively and negatively charged. The positive metal mesh 9 and the negative metal mesh 10 are separated by an insulating plate. The gas with positive charge and negative charge respectively flows into the agglomerator 4, and the gas impacts on the blades of the impeller to make the impeller rotate, so that the particles with different charges are fully mixed and condensed, so that the particle size of the particles in the gas becomes larger. Realize the growth of particles, so as to facilitate the collection and processing of subsequent particles. The gas containing particles with larger particle size flows tangentially into the electrostatic cyclone particle catcher assembly 6, and the schematic diagram of the movement of the gas in the electrostatic cyclone particle catcher is shown in Figure 4. The particles in the gas are under the influence of centrifugal force and electrostatic field force. Under the action, it is thrown onto the inner wall of the outer cylinder 14, and falls into the particle collector 16 under the action of gravity. In addition, the electrostatic cyclone particle capture assembly still has the advantages of the traditional cyclone dust collector, has the function of automatic dust removal, and does not generate secondary dust. Finally, the gas that has undergone the primary particle capture flows out of the gas outlet of the electrostatic cyclone particle catcher assembly and flows into the electromagnetic particle catcher assembly 7 . Particles that have not been effectively removed in the gas are positively charged through the electrode 23 in the positive charge area, and then the particles with positive charges enter the uniform magnetic field 35, and are deflected under the joint action of Lorentz magnetic force and Coulomb force, and are respectively deflected upward and downward for collection. plate. Then the remaining positively charged particles enter the negatively charged area 31, are adsorbed in the negatively charged area 31, and finally the gas that meets the emission requirements is discharged from the smog particle collection and treatment device by the air outlet 29 of the electromagnetic particle catcher assembly. . The selection and setting of the pair of electrodes and the electromagnetic coil are prior art in this field, and those skilled in the art can select and set according to the prior art.

在本发明中,将静电除尘器与旋风除尘器结合起来,克服了他们单独作用时的缺陷,并对其结构进行了优化,本发明的突出特点之一即为先将小的颗粒进行聚合,使颗粒的粒径变大,这样有利于旋风静电颗粒捕捉器总成对颗粒进行捕捉与收集,大大提高了颗粒的收集效率。另外在气流速很低的情况下,电子控制单元39将空气流量计2的信息进行分析,然后控制第一空气阀5的开度,从而使气体的流速增加,使颗粒所受离心力变大,有利于颗粒的分离,从而提高静电旋风颗粒捕捉器的捕捉效率,而当气体流速较快时,电子控制单元39控制第一空气阀5的开度,改变气体的流速并改变电磁颗粒捕捉器总成7中磁场区32中匀强磁场35的磁场强度,使颗粒在磁场区32所受洛仑磁力变大,增强磁场区32的颗粒捕捉能力,从而弥补由于气体流速增加而造成静电捕捉效率的降低,从而使整个雾霾颗粒收集处理装置的颗粒捕捉能力得以提升。在电磁颗粒捕捉总成中,吸附的颗粒主要存在于磁场区32和负电荷区,这样时间长了必然会造成背压的增加。因此,经过试验,设定一个合理的时间,然后将设定好的时间存储在电子控制单元39内,当达到设定的时间后,电子控制单元39发出指令,关闭阀门28,并打开旁通阀34,使从静电旋风颗粒捕捉器总成6中出来的气体经旁通阀34流走。另外电子控制单元39控制第二空气阀21使其打开,供给一定量的二次空气,电子控制单元39控制电热丝30对负电荷区31和磁场区32进行加热,使其上面吸附的颗粒可以得以充分的燃烧,设定一定的燃烧时间存储于电子控制单元39内,当燃烧完全后,电子控制单元39控制阀门28使其打开,使燃烧后的气体排出,并关闭旁通阀34和第二空气阀21。由于这段燃烧的时间是非常短的,并且气体已经经过静电旋风颗粒捕捉器总成6的处理,因此在这段颗粒的燃烧过程中排出的气体中颗粒的含量其实是很少,并且显著减小了排气背压。 In the present invention, the electrostatic precipitator and the cyclone dust collector are combined to overcome the defects when they act alone, and optimize their structure. One of the outstanding features of the present invention is that the small particles are first aggregated, The size of the particles becomes larger, which is beneficial to the cyclone electrostatic particle catcher assembly to capture and collect the particles, and greatly improves the collection efficiency of the particles. In addition, when the air flow rate is very low, the electronic control unit 39 analyzes the information of the air flow meter 2, and then controls the opening of the first air valve 5, thereby increasing the flow rate of the gas and increasing the centrifugal force on the particles. It is beneficial to the separation of particles, thereby improving the capture efficiency of the electrostatic cyclone particle catcher, and when the gas flow rate is fast, the electronic control unit 39 controls the opening of the first air valve 5, changes the flow rate of the gas and changes the overall flow rate of the electromagnetic particle catcher. The magnetic field strength of the uniform magnetic field 35 in the magnetic field area 32 in the formation of 7 makes the Lorent magnetic force suffered by the particles in the magnetic field area 32 larger, and enhances the particle capture ability of the magnetic field area 32, thereby making up for the increase in the gas flow rate. Therefore, the particle capture capacity of the entire smog particle collection and treatment device can be improved. In the electromagnetic particle capture assembly, the adsorbed particles mainly exist in the magnetic field region 32 and the negative charge region, which will inevitably cause an increase in back pressure after a long time. Therefore, after testing, a reasonable time is set, and then the set time is stored in the electronic control unit 39. When the set time is reached, the electronic control unit 39 issues an instruction to close the valve 28 and open the bypass The valve 34 makes the gas from the electrostatic cyclone particle catcher assembly 6 flow away through the bypass valve 34 . In addition, the electronic control unit 39 controls the second air valve 21 to open to supply a certain amount of secondary air. The electronic control unit 39 controls the heating wire 30 to heat the negative charge area 31 and the magnetic field area 32, so that the particles adsorbed on it can be To achieve sufficient combustion, a certain combustion time is set and stored in the electronic control unit 39. When the combustion is complete, the electronic control unit 39 controls the valve 28 to open to discharge the burned gas, and close the bypass valve 34 and the second Two air valves 21. Since the combustion time of this period is very short, and the gas has been treated by the electrostatic cyclone particle catcher assembly 6, the content of particles in the gas discharged during this period of particle combustion is actually very small, and it is significantly reduced. Reduced exhaust back pressure.

实施例2: Example 2:

还可将该装置的装置进气口与柴油机等其它产生废气的设备的废气排放出口相连接,可以大幅减少废气中的颗粒物、炭烟含量以及PM2.5的排放,并且不会造成二次扬尘污染。 The air inlet of the device can also be connected with the exhaust outlet of other equipment that produces exhaust gas such as diesel engines, which can greatly reduce the particulate matter, soot content and PM2.5 emissions in the exhaust gas, and will not cause secondary dust. pollute.

以上显示和描述了本发明的基本原理、主要特征和本发明的优点。本行业的技术人员应该了解,本发明不受上述实施例的限制,上述实施例和说明书中描述的只是说明本发明的原理,在不脱离本发明精神和范围的前提下本发明还会有各种变化和改进,这些变化和改进都落入要求保护的本发明范围内。本发明要求保护范围由所附的权利要求书及其等同物界定。 The basic principles, main features and advantages of the present invention have been shown and described above. Those skilled in the industry should understand that the present invention is not limited by the above-mentioned embodiments, and that described in the above-mentioned embodiments and the description only illustrates the principles of the present invention, and the present invention also has various aspects without departing from the spirit and scope of the present invention. Variations and improvements all fall within the scope of the claimed invention. The protection scope of the present invention is defined by the appended claims and their equivalents.

Claims (8)

1. a haze powder collection treatment device, it is characterized in that: comprise device suction port, charged region assembly, flokcculator, electrostatic whirlwind particle trap assembly, electromagnetic particle catcher assembly and device air outlet, described device suction port is connected with charged region assembly, flokcculator is provided with between described charged region assembly and electrostatic whirlwind particle trap assembly, described electrostatic whirlwind particle trap assembly is connected with electromagnetic particle catcher assembly, and one end of described electromagnetic particle catcher assembly is provided with device air outlet.
2. haze powder collection treatment device according to claim 1, it is characterized in that: also comprise electronic control unit, Air flow meter and the first air valve, described Air flow meter is arranged on device suction port, and the signal of described Air flow meter goes out end and is connected with the signal input part of electronic control unit.
3. haze powder collection treatment device according to claim 1, it is characterized in that: described charged region assembly comprises cathode metal net, negative metal net, insulation board and shell, described insulation board is arranged in the middle of shell, charged region is separated into two-part, evenly be provided with wire netting in every part, what what the wire netting be separated was connected with positive electrode be connected with negative electrode for cathode metal net is negative metal net.
4. haze powder collection treatment device according to claim 1, it is characterized in that: in the housing of described flokcculator, be provided with the impeller be made up of impeller blade and impeller shaft, be provided with the first air valve between described flokcculator and electrostatic whirlwind particle trap assembly, the signal of the first described air valve goes out end and enters end with the signal of electronic control unit and be connected.
5. haze powder collection treatment device according to claim 1, it is characterized in that: described electrostatic whirlwind particle trap assembly comprises electrostatic whirlwind particle trap assembly suction port, urceolus, inner core, particle collector, electrostatic whirlwind particle trap assembly air outlet, arista electrode and newel, described electrostatic whirlwind particle trap assembly suction port is connected with flokcculator air outlet, described inner core is arranged on one end in urceolus and is connected with electrostatic whirlwind particle trap assembly air outlet, newel is provided with in described urceolus, the surface uniform of described newel is provided with arista electrode, particle collector is provided with bottom described urceolus.
6. haze powder collection treatment device according to claim 1, is characterized in that: described electromagnetic particle catcher assembly is divided into Pregionp, field regions, negative charge region and heating-up zone, comprise electromagnetic particle catcher assembly suction port, second air valve, Pregionp shell, Pregionp electrode, heating-up zone shell, negative charge region electrode, valve, electromagnetic particle catcher assembly air outlet, electric heating wire, upper and lower collecting board, bypass valve, uniform magnetic field and by-pass, described electromagnetic particle catcher assembly suction port is connected with electrostatic whirlwind particle trap assembly air outlet, described electromagnetic particle catcher assembly suction port is provided with by-pass and secondary air entrance, the second air valve is provided with in described secondary air entrance, the described by-pass the other end is connected with electromagnetic particle catcher assembly air outlet, described electromagnetic particle catcher assembly suction port is connected with Pregionp shell, described Pregionp electrode is evenly distributed in the shell of Pregionp, described is provided with uniform magnetic field and negative charge region electrode up and down between collecting board, described collecting board is up and down outward heating-up zone, inside be provided with electric heating wire, described electromagnetic particle catcher assembly air outlet place is provided with valve, is provided with bypass valve in described by-pass.
7. haze powder collection treatment device according to claim 1, is characterized in that: described impeller, bypass valve, valve, the first air valve are connected with the signal output part of electronic control unit with the signal input part of the second air valve.
8. haze powder collection treatment device according to claim 1, is characterized in that: described charged region assembly shell, flokcculator shell, impeller blade and Pregionp shell adopt insulating material to make.
CN201510291216.2A 2015-06-01 2015-06-01 A kind of haze powder collection processing unit Expired - Fee Related CN104963746B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201510291216.2A CN104963746B (en) 2015-06-01 2015-06-01 A kind of haze powder collection processing unit

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201510291216.2A CN104963746B (en) 2015-06-01 2015-06-01 A kind of haze powder collection processing unit

Publications (2)

Publication Number Publication Date
CN104963746A true CN104963746A (en) 2015-10-07
CN104963746B CN104963746B (en) 2017-11-10

Family

ID=54217805

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201510291216.2A Expired - Fee Related CN104963746B (en) 2015-06-01 2015-06-01 A kind of haze powder collection processing unit

Country Status (1)

Country Link
CN (1) CN104963746B (en)

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN105240090A (en) * 2015-10-28 2016-01-13 重庆工商大学 Technique method used for removing automobile tail gas particles
CN106769739A (en) * 2017-01-19 2017-05-31 兰州大学 A kind of system for determining haze charged particle percentage
CN108654838A (en) * 2018-04-02 2018-10-16 中山市雅乐思商住电器有限公司 Flue gas purification system and method thereof
CN116297066A (en) * 2023-03-22 2023-06-23 滨州市特种设备检验研究院 Boiler flue gas detection device with flue gas filtering capability

Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS63221823A (en) * 1987-03-10 1988-09-14 Toyota Motor Corp Dust capturing method and its device
FR2884857B1 (en) * 2005-04-26 2007-06-22 Renault Sas INERTIALLY SEPARATING ELEMENT DEVICE FOR FILTERING AND ELIMINATING PARTICLES CONTAINED IN EXHAUST GASES
CN102770193A (en) * 2010-02-26 2012-11-07 英派尔科技开发有限公司 Nanoparticle separation
CN103623669A (en) * 2013-12-10 2014-03-12 福建龙净环保股份有限公司 Electric-bag composite dust collector
CN104174492A (en) * 2014-08-22 2014-12-03 成都代代吉前瞻科技股份有限公司 Efficient electrostatic-dielectrophoresis deduster
CN104588209A (en) * 2014-12-29 2015-05-06 上海安平静电科技有限公司 Method for removing fine particulate matters in air under condition of home environment

Patent Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS63221823A (en) * 1987-03-10 1988-09-14 Toyota Motor Corp Dust capturing method and its device
FR2884857B1 (en) * 2005-04-26 2007-06-22 Renault Sas INERTIALLY SEPARATING ELEMENT DEVICE FOR FILTERING AND ELIMINATING PARTICLES CONTAINED IN EXHAUST GASES
CN102770193A (en) * 2010-02-26 2012-11-07 英派尔科技开发有限公司 Nanoparticle separation
CN103623669A (en) * 2013-12-10 2014-03-12 福建龙净环保股份有限公司 Electric-bag composite dust collector
CN104174492A (en) * 2014-08-22 2014-12-03 成都代代吉前瞻科技股份有限公司 Efficient electrostatic-dielectrophoresis deduster
CN104588209A (en) * 2014-12-29 2015-05-06 上海安平静电科技有限公司 Method for removing fine particulate matters in air under condition of home environment

Non-Patent Citations (2)

* Cited by examiner, † Cited by third party
Title
竹涛等: "电凝并技术脱除PM2.5的研究现状及发展方向", 《洁净煤技术》 *
陈王锋: "旋风静电空气滤清器的设计及流场防真", 《CNKI的优秀硕士学位论文全库》 *

Cited By (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN105240090A (en) * 2015-10-28 2016-01-13 重庆工商大学 Technique method used for removing automobile tail gas particles
CN105240090B (en) * 2015-10-28 2018-04-24 重庆工商大学 A kind of technical method for being used to remove Vehicle Exhaust Particulate
CN106769739A (en) * 2017-01-19 2017-05-31 兰州大学 A kind of system for determining haze charged particle percentage
CN106769739B (en) * 2017-01-19 2024-01-23 兰州大学 System for determining percentage of haze charged particles
CN108654838A (en) * 2018-04-02 2018-10-16 中山市雅乐思商住电器有限公司 Flue gas purification system and method thereof
CN116297066A (en) * 2023-03-22 2023-06-23 滨州市特种设备检验研究院 Boiler flue gas detection device with flue gas filtering capability
CN116297066B (en) * 2023-03-22 2024-04-05 新疆新伊碳能环保科技股份有限公司 Boiler flue gas detection device with flue gas filtering capability

Also Published As

Publication number Publication date
CN104963746B (en) 2017-11-10

Similar Documents

Publication Publication Date Title
CN104963746B (en) A kind of haze powder collection processing unit
CN102773162B (en) Method for removing fine particles and heavy metals in coal fume
CN102631990A (en) Method and device for efficiently catching nanometer micro-particles
CN103447153A (en) Electronic dust remover
CN106362880B (en) Bipolar charge-cyclone separator and technique for flue gas dedusting
CN105921276A (en) Fine particle rotational flow type electric agglomeration dust removing and collecting device
CN107243410A (en) A kind of new pole plate electric dust collector
CN104069712A (en) Chemical coagulation-based 'electricity-bag' integrated compound dust removing process
CN106731434A (en) A kind of combined ultra-fine grain coalescence case
CN104069713A (en) Coagulation-enhanced electricity-bag dust removing process
CN106731435A (en) A kind of angle-style ultra-fine grain coalescence case
US7435288B2 (en) System for filtering particulate matter of diesel particulate filter
CN206746199U (en) Double filter screen electrocoagulation fine particle cleaning equipment
CN106567761A (en) A composite vehicle exhaust particle filter device
CN201470284U (en) Electric bag hybrid dust collector
CN105240090B (en) A kind of technical method for being used to remove Vehicle Exhaust Particulate
CN207655319U (en) A kind of electrostatic precipitation system
CN106512634A (en) Streamline ultrafine particle coagulation box
CN207238261U (en) A kind of new pole plate electric dust collector
CN205225386U (en) Novel absorption of high -efficient automobile exhaust particulate matter device
CN106523075A (en) Wire-pipe type diesel vehicle tail gas particle trap based on corona discharge
CN206382119U (en) A kind of device of pulse corona charge removing sintering flue gas fine particulate matter
CN107664049A (en) A kind of pressure swing type diesel particulation Electrostatic regenerative system and its control method
CN205340456U (en) Flue gas dust removal system
CN206175030U (en) Combined type automobile exhaust particulate filter assembly

Legal Events

Date Code Title Description
C06 Publication
PB01 Publication
C10 Entry into substantive examination
SE01 Entry into force of request for substantive examination
GR01 Patent grant
GR01 Patent grant
CF01 Termination of patent right due to non-payment of annual fee

Granted publication date: 20171110

Termination date: 20200601

CF01 Termination of patent right due to non-payment of annual fee