CN105921276A - Fine particle rotational flow type electric agglomeration dust removing and collecting device - Google Patents

Fine particle rotational flow type electric agglomeration dust removing and collecting device Download PDF

Info

Publication number
CN105921276A
CN105921276A CN201610341415.4A CN201610341415A CN105921276A CN 105921276 A CN105921276 A CN 105921276A CN 201610341415 A CN201610341415 A CN 201610341415A CN 105921276 A CN105921276 A CN 105921276A
Authority
CN
China
Prior art keywords
housing
coalescence
flow type
friction
coagulation
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
CN201610341415.4A
Other languages
Chinese (zh)
Other versions
CN105921276B (en
Inventor
李海生
武涛
沈子凡
刘宇
梅玉坤
石科军
刁瑞
姜金乌
陈英华
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.)
China University of Mining and Technology CUMT
Original Assignee
China University of Mining and Technology CUMT
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 China University of Mining and Technology CUMT filed Critical China University of Mining and Technology CUMT
Priority to CN201610341415.4A priority Critical patent/CN105921276B/en
Publication of CN105921276A publication Critical patent/CN105921276A/en
Application granted granted Critical
Publication of CN105921276B publication Critical patent/CN105921276B/en
Expired - Fee Related legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Classifications

    • BPERFORMING OPERATIONS; TRANSPORTING
    • B03SEPARATION OF SOLID MATERIALS USING LIQUIDS OR USING PNEUMATIC TABLES OR JIGS; MAGNETIC OR ELECTROSTATIC SEPARATION OF SOLID MATERIALS FROM SOLID MATERIALS OR FLUIDS; SEPARATION BY HIGH-VOLTAGE ELECTRIC FIELDS
    • B03CMAGNETIC OR ELECTROSTATIC SEPARATION OF SOLID MATERIALS FROM SOLID MATERIALS OR FLUIDS; SEPARATION BY HIGH-VOLTAGE ELECTRIC FIELDS
    • B03C3/00Separating dispersed particles from gases or vapour, e.g. air, by electrostatic effect
    • B03C3/34Constructional details or accessories or operation thereof
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B03SEPARATION OF SOLID MATERIALS USING LIQUIDS OR USING PNEUMATIC TABLES OR JIGS; MAGNETIC OR ELECTROSTATIC SEPARATION OF SOLID MATERIALS FROM SOLID MATERIALS OR FLUIDS; SEPARATION BY HIGH-VOLTAGE ELECTRIC FIELDS
    • B03CMAGNETIC OR ELECTROSTATIC SEPARATION OF SOLID MATERIALS FROM SOLID MATERIALS OR FLUIDS; SEPARATION BY HIGH-VOLTAGE ELECTRIC FIELDS
    • B03C3/00Separating dispersed particles from gases or vapour, e.g. air, by electrostatic effect
    • B03C3/01Pretreatment of the gases prior to electrostatic precipitation

Landscapes

  • Electrostatic Separation (AREA)

Abstract

The invention discloses a fine particle rotational flow type electric agglomeration dust removing and collecting device. The device is arranged at the front portion of an electric precipitator. Fine particles are carried by airflow to enter a cylindrical shell in the tangential direction. Friction bars and arista electrodes are arranged on the inner wall face of the shell, the particles collide with and make contact with the friction bars to rub electrical charges in the gradual downward rotational flow type moving process, and the arista electrodes intensify the electrical charges under the action of corona. The charged particles enter a pipeline connected through at least one pair of Venturi tubes. High-voltage electrode plates opposite in polarity are arranged on the two sides of the Venturi tubes, consequently, the particles generate collision and coagulation through the action of electric field force in the opposite directions, and the particles are conveyed into the electric precipitator through the pipeline to be collected and subjected to dust removing. The problem that the electrical charges of the fine particles are not sufficient is solved. The collision frequency in the particle coagulation process is increased, particle aggregates with the large granularity can be obtained, the dust removing efficiency of the electric precipitator is improved, the concentration of the fine particles in air is reduced, and the environment pollution is reduced.

Description

A kind of subparticle spiral-flow type coagulation dedusting collection device also
Technical field
The present invention relates to a kind of subparticle spiral-flow type coagulation dedusting collection device also, relate to field of environment engineering technology, particularly pellet in removing coal-fired power plant dust, it is possible to obtain preferably trap effect, can be also used for the dedusting in commercial production to collect, reduce environmental pollution.
Background technology
The main source of subparticle, is the residue discharged through burning during daily generating, commercial production, motor vehicle exhaust emission etc., mostly containing noxious substances such as heavy metals, health is brought harm and atmosphere pollution.A large amount of subparticles are gathered into flue dust, existing flue dust minimizing technology is mainly by cleaners such as electric cleaner, sack cleaner and water dedusters, although these equipment are up to 99.9% for the collection efficiency of flue dust, but the subparticle for 0.1-1 micron, efficiency of dust collection is less than 85%, and these subparticles bring the reason of significant damage precisely with human body and environment.Subparticle is carried out coalescence, forms the bigger aggregation of granularity and can improve the efficiency of dust collection of cleaner unit, it is particularly possible to improve the collection efficiency to subparticle.
Coalescence method mainly have heat setting also, sound coalescence and coagulation also, consider technical complexity and economic consumption degree, coagulation is a kind of more feasible coalescence method.Coagulation be by subparticle carries out pre electrified, increases the coalescence degree between granule so that it is be gathered into big granularity aggregation, improves subparticle efficiency of dust collection.In existing coagulation equipment, subparticle the charged stage can not reach charged fully, and during coalescence, subparticle can not fully collide, so the grain graininess of coalescence does not reaches requirement of gathering dust, causes subparticle dust-collecting efficiency relatively low.
Summary of the invention
In order to overcome above-mentioned the deficiencies in the prior art, it is an object of the invention to provide a kind of subparticle spiral-flow type coagulation dedusting collection device also.
The technical solution adopted in the present invention is: a kind of subparticle spiral-flow type coagulation dedusting collection device also, coagulation device are installed on the charging aperture of electric cleaner, it is characterized in that, described coagulation device include triboelectrificationdevice device and the coalescence device being linked in sequence, and coalescence device is connected with electric cleaner;Described triboelectrificationdevice device includes housing, entrained particle entrance, the arista electrode of band positive corona and friction-bar;Housing is cylindrical enclosure structure, and its top is provided with entrained particle entrance, and Way in is the tangential direction of cylindrical housings;Described arista electrode and friction-bar are located in housing, and arista electrode and friction-bar are crisscross arranged along the axial and circumferential of housing respectively, and one end of arista electrode and friction-bar is connected with inner walls, the center of the other end parallel sensing housing;Described coalescence device is made up of with the Venturi tube of rightabout high voltage electric field is end to end least one set;The Venturi tube being positioned at coalescence device top is provided with funnel-form union joint, and the opening of union joint is connected with housing;The Venturi tube connection being positioned at coalescence device bottom has arc pipe, and the end of arc pipe is set to funnel-form, and is connected with the feeding mouth of electric cleaner;In work process, granule is under air-flow drives, in tangential direction enters housing, within it wall forms annularly flow, granule and the friction-bar being arranged on inner walls face carry out frictional impact, and strengthen charged under arista electrode corona effect, electrically charged particle in high voltage electric field because of by electric field force effect in opposite direction, electrically charged particle produces and collides and coalescence, and the bulky grain after coalescence is sent in electric cleaner by pipeline and is collected dedusting.
The arista electrode and the friction-bar that are positioned at same layer are staggered with 90 degree successively along housing circumference.
The space that the length setting of described arista electrode can be full of housing with corona produced by it is as the criterion.
Opposite polarity battery lead plate is installed in the both sides of each Venturi tube, and adjacent two Venturi tubes are positioned at the battery lead plate opposite polarity of the same side, form two sections of electric fields that direction of an electric field is contrary.
Described Venturi tube is connected with housing and electric cleaner by flange, passes through Flange joint between adjacent Venturi tube.
Compared with prior art, the invention has the beneficial effects as follows: subparticle is under air-flow rolling action, tangentially into the swirling motion done after Closed cylindrical shell body straight down, owing to arista electrode and friction-bar are so that 90 degree of angles are uniformly staggered and stacked distribution is in inner walls face, make in granule motor process through arista electrode corona zone, simultaneously carrying out frictional impact with friction-bar, granule can sufficiently carry out corona charging and friction charged, thus improves charging particle effect.Charged particle, after entering Venturi tube, reduces along with pipeline section is long-pending, adds granule density and mutual collision frequency.It is mounted with charged opposite polarity battery lead plate in pipeline both sides, defines in opposite direction two section electric field.Electrically charged particle, under electric field force effect, produces and collides and coalescence, and the bulky grain after coalescence is sent in electric cleaner by pipeline and is collected dedusting, improves efficiency of dust collection.
Accompanying drawing explanation
Fig. 1 is a kind of subparticle spiral-flow type coagulation dedusting collection device schematic diagram also.
Fig. 2 is coagulation the apparatus structure schematic diagram of a kind of subparticle spiral-flow type coagulation dedusting collection device also.
Fig. 3 be a kind of subparticle spiral-flow type coagulation and dedusting collection device coagulation and device top view.
In accompanying drawing, the labelling of each parts is as follows: 1, coagulation device, 2, electric cleaner, 3, housing, 4, entrained particle entrance, 5, arista electrode, 6, friction-bar, 7, Venturi tube, 8, first paragraph positive plate, 9, second segment negative plate, 10, pipeline, 11, second segment positive plate, 12, first paragraph negative plate.
Detailed description of the invention
The present invention is described in detail below in conjunction with the accompanying drawings.
Fig. 1 is a kind of subparticle spiral-flow type coagulation dedusting collection device schematic diagram also, coagulation device 1 are positioned at electric cleaner 2 front end, subparticle in flue dust is after coagulation device 1 process, and subparticle is gathered into granularity larger particles, can be collected by electric cleaner 2.
Coagulation device 1 are installed on triboelectrificationdevice device and the coalescence device that the charging aperture of electric cleaner 2, described coagulation device 1 include being linked in sequence, and coalescence device is connected with electric cleaner 1;Described triboelectrificationdevice device includes housing 3, entrained particle entrance 4, the arista electrode 5 of band positive corona and friction-bar 6;Housing 3 is cylindrical enclosure structure, and its top is provided with entrained particle entrance 4, and Way in is the tangential direction of cylindrical housings 3;Described arista electrode 5 and friction-bar 4 are located in housing 3, and arista electrode 5 and friction-bar 6 are crisscross arranged along the axial and circumferential of housing 3 respectively, and one end of arista electrode 5 and friction-bar 4 is connected with housing 3 inwall, the center of the other end parallel sensing housing 3;Described coalescence device is made up of with the Venturi tube 7 of rightabout high voltage electric field is end to end least one set;The Venturi tube 7 being positioned at coalescence device top is provided with funnel-form union joint, and the opening of union joint and housing 3 are by Flange joint, and adjacent Venturi tube 7 passes through Flange joint;The bottom of the Venturi tube 7 being positioned at bottom is provided with arc pipe 10, and the end of arc pipe 10 is set to funnel-form, and passes through Flange joint with the feeding mouth of electric cleaner 1;In work process, granule is under air-flow drives, in tangential direction enters housing 3, within it wall forms annularly flow, granule carries out frictional impact with the friction-bar 6 being arranged on housing 3 internal face, and strengthens charged under arista electrode 5 corona effect, electrically charged particle in high voltage electric field because of by electric field force effect in opposite direction, electrically charged particle produces and collides and coalescence, and the bulky grain after coalescence is sent in electric cleaner 2 by pipeline and is collected dedusting.
As it is shown on figure 3, be positioned at the arista electrode 5 of same layer and friction-bar 6 is staggered with 90 degree successively along housing 3 circumference.The space that the length setting of described arista electrode 5 can be full of housing 3 with corona produced by it is as the criterion.
Opposite polarity battery lead plate is installed in the both sides of each Venturi tube 7, and adjacent two Venturi tubes 7 are positioned at the battery lead plate opposite polarity of the same side, form two sections of electric fields that direction of an electric field is contrary.As in figure 2 it is shown, end to end two sections of Venturi tubes 7, the side of the preceding paragraph section Venturi tube 7 arranges first paragraph positive plate 8, and its opposite side is symmetrical arranged first paragraph negative plate 12;The lower section of the side correspondence first paragraph positive plate 8 of next section of Venturi tube 7 arranges second segment negative plate 9, and the lower section of opposite side correspondence first paragraph negative plate 12 arranges second segment positive plate 11.
Granule, under air-flow rolling action, is entered in cylindrical housings 3 by entrained particle entrance 4 in tangential direction, granule during the swirling motion of inner walls face, charging particle under the corona effect of arista electrode 5, can also collide with friction-bar 6 and charged simultaneously.After charged particle enters the Venturi tube 7 being connected bottom cylindrical housings 3, owing to pipeline section reduces, granule density increase makes charged particle more be fully contacted.Because battery lead plate mounting means difference causes first paragraph electric field, second segment direction of an electric field contrary, when charged particle is when by two ends electric field, by electric field force effect in opposite direction, opposite sex charged particle produces and collides and coalescence.The bulky grain formed is entered in electric cleaner 2 by pipeline 10 and removes.

Claims (5)

1. a subparticle spiral-flow type coagulation dedusting collection device also, coagulation device are installed on the charging aperture of electric cleaner, it is characterised in that described coagulation device include triboelectrificationdevice device and the coalescence device being linked in sequence, and coalescence device is connected with electric cleaner;Described triboelectrificationdevice device includes housing, entrained particle entrance, the arista electrode of band positive corona and friction-bar;Housing is cylindrical enclosure structure, and its top is provided with entrained particle entrance, and Way in is the tangential direction of cylindrical housings;Described arista electrode and friction-bar are located in housing, and arista electrode and friction-bar are crisscross arranged along the axial and circumferential of housing respectively, and one end of arista electrode and friction-bar is connected with inner walls, the center of the other end parallel sensing housing;Described coalescence device is made up of with the Venturi tube of rightabout high voltage electric field is end to end least one set;The Venturi tube being positioned at coalescence device top is provided with funnel-form union joint, and the opening of union joint is connected with housing;The Venturi tube connection being positioned at coalescence device bottom has arc pipe, and the end of arc pipe is set to funnel-form, and is connected with the feeding mouth of electric cleaner;In work process, granule is under air-flow drives, in tangential direction enters housing, within it wall forms annularly flow, granule and the friction-bar being arranged on inner walls face carry out frictional impact, and strengthen charged under arista electrode corona effect, electrically charged particle in high voltage electric field because of by electric field force effect in opposite direction, electrically charged particle produces and collides and coalescence, and the bulky grain after coalescence is sent in electric cleaner by pipeline and is collected dedusting.
Subparticle spiral-flow type coagulation the most according to claim 1 dedusting collection device also, it is characterised in that: the arista electrode and the friction-bar that are positioned at same layer are staggered with 90 degree successively along housing circumference.
Subparticle spiral-flow type coagulation the most according to claim 1 dedusting collection device also, it is characterised in that: the space that the length setting of described arista electrode can be full of housing with corona produced by it is as the criterion.
Subparticle spiral-flow type coagulation the most according to claim 1 dedusting collection device also, it is characterized in that: opposite polarity battery lead plate is installed in the both sides of each Venturi tube, and adjacent two Venturi tubes are positioned at the battery lead plate opposite polarity of the same side, form two sections of electric fields that direction of an electric field is contrary.
Subparticle spiral-flow type coagulation the most according to claim 1 dedusting collection device also, it is characterised in that: described Venturi tube is connected with housing and electric cleaner by flange, passes through Flange joint between adjacent Venturi tube.
CN201610341415.4A 2016-05-23 2016-05-23 Fine particle rotational flow type electric agglomeration dust removing and collecting device Expired - Fee Related CN105921276B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201610341415.4A CN105921276B (en) 2016-05-23 2016-05-23 Fine particle rotational flow type electric agglomeration dust removing and collecting device

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201610341415.4A CN105921276B (en) 2016-05-23 2016-05-23 Fine particle rotational flow type electric agglomeration dust removing and collecting device

Publications (2)

Publication Number Publication Date
CN105921276A true CN105921276A (en) 2016-09-07
CN105921276B CN105921276B (en) 2017-05-17

Family

ID=56841048

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201610341415.4A Expired - Fee Related CN105921276B (en) 2016-05-23 2016-05-23 Fine particle rotational flow type electric agglomeration dust removing and collecting device

Country Status (1)

Country Link
CN (1) CN105921276B (en)

Cited By (9)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN106178799A (en) * 2016-09-13 2016-12-07 成都创慧科达科技有限公司 A kind of thermal power plant environment-protective circulating dust arrester
CN107138016A (en) * 2017-05-08 2017-09-08 浙江大学 Based on many particulate matter coalescence reunion intensifying devices promoted and method
CN107349729A (en) * 2017-06-29 2017-11-17 苏州艾特斯环保设备有限公司 A kind of electrostatic charged spray method
CN108787169A (en) * 2018-07-25 2018-11-13 安徽卓煌机械设备有限公司 A kind of sieve-board type finished ground cement electric dust collecting means
CN109883910A (en) * 2019-01-29 2019-06-14 黑龙江科技大学 A kind of electrostatic induction apparatus for measuring dust concentration with pre electrified
CN109916789A (en) * 2019-01-29 2019-06-21 黑龙江科技大学 A kind of low concentration small particle dust investigating based on electrostatic induction
CN109967239A (en) * 2017-12-27 2019-07-05 宁波方太厨具有限公司 A kind of microparticle purification device based on electric coagulating technique
CN111604176A (en) * 2020-04-23 2020-09-01 中国矿业大学 Recyclable environment-friendly device and method for cyclone electrocoagulation and industrial dedusting
CN112285004A (en) * 2020-09-25 2021-01-29 台州市中心医院(台州学院附属医院) Biosafety device for flow cytometer

Citations (7)

* 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
KR20050112535A (en) * 2004-05-27 2005-12-01 한국기계연구원 Apparatus for removing the harmful fine particles with combined negative and positive dielectric agglomeration precipitation and method for capturing the same
US20110000368A1 (en) * 2009-07-01 2011-01-06 Fernando Ray Tollens Dynamic electrostatic apparatus for purifying air using electronically charged droplets
CN202270577U (en) * 2011-08-26 2012-06-13 浙江菲达脱硫工程有限公司 Device for removing PM2.5 (particle matter less than 2.5 micrometers in diameter) in smoke
CN102772971A (en) * 2011-12-15 2012-11-14 中国矿业大学(北京) Superfine particulate matter purifying device
CN104984825A (en) * 2015-07-20 2015-10-21 中国矿业大学 Friction electric separation method and device for micro-fine particle damp materials
CN204746584U (en) * 2015-05-20 2015-11-11 李轼 Electric coalescence composite set of aerosol particle lotus

Patent Citations (7)

* 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
KR20050112535A (en) * 2004-05-27 2005-12-01 한국기계연구원 Apparatus for removing the harmful fine particles with combined negative and positive dielectric agglomeration precipitation and method for capturing the same
US20110000368A1 (en) * 2009-07-01 2011-01-06 Fernando Ray Tollens Dynamic electrostatic apparatus for purifying air using electronically charged droplets
CN202270577U (en) * 2011-08-26 2012-06-13 浙江菲达脱硫工程有限公司 Device for removing PM2.5 (particle matter less than 2.5 micrometers in diameter) in smoke
CN102772971A (en) * 2011-12-15 2012-11-14 中国矿业大学(北京) Superfine particulate matter purifying device
CN204746584U (en) * 2015-05-20 2015-11-11 李轼 Electric coalescence composite set of aerosol particle lotus
CN104984825A (en) * 2015-07-20 2015-10-21 中国矿业大学 Friction electric separation method and device for micro-fine particle damp materials

Cited By (13)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN106178799B (en) * 2016-09-13 2019-03-08 成都创慧科达科技有限公司 A kind of thermal power plant's environment-protective circulating dust-extraction unit
CN106178799A (en) * 2016-09-13 2016-12-07 成都创慧科达科技有限公司 A kind of thermal power plant environment-protective circulating dust arrester
CN107138016A (en) * 2017-05-08 2017-09-08 浙江大学 Based on many particulate matter coalescence reunion intensifying devices promoted and method
CN107349729A (en) * 2017-06-29 2017-11-17 苏州艾特斯环保设备有限公司 A kind of electrostatic charged spray method
CN109967239A (en) * 2017-12-27 2019-07-05 宁波方太厨具有限公司 A kind of microparticle purification device based on electric coagulating technique
CN109967239B (en) * 2017-12-27 2023-11-17 宁波方太厨具有限公司 Microparticle purifier based on electrocoagulation technology
CN108787169A (en) * 2018-07-25 2018-11-13 安徽卓煌机械设备有限公司 A kind of sieve-board type finished ground cement electric dust collecting means
CN109916789A (en) * 2019-01-29 2019-06-21 黑龙江科技大学 A kind of low concentration small particle dust investigating based on electrostatic induction
CN109883910A (en) * 2019-01-29 2019-06-14 黑龙江科技大学 A kind of electrostatic induction apparatus for measuring dust concentration with pre electrified
CN111604176A (en) * 2020-04-23 2020-09-01 中国矿业大学 Recyclable environment-friendly device and method for cyclone electrocoagulation and industrial dedusting
CN111604176B (en) * 2020-04-23 2021-10-29 中国矿业大学 Recyclable environment-friendly device and method for cyclone electrocoagulation and industrial dedusting
CN112285004A (en) * 2020-09-25 2021-01-29 台州市中心医院(台州学院附属医院) Biosafety device for flow cytometer
CN112285004B (en) * 2020-09-25 2023-10-10 台州市中心医院(台州学院附属医院) Biosafety device for flow cytometry

Also Published As

Publication number Publication date
CN105921276B (en) 2017-05-17

Similar Documents

Publication Publication Date Title
CN105921276B (en) Fine particle rotational flow type electric agglomeration dust removing and collecting device
CA2685734C (en) Process of electrostatic recirculation for dedusting and gas cleaning and device
CN103447153A (en) Electronic dust remover
CN104815755A (en) Novel electrostatic dust removing structure
CN202006137U (en) Ultrafine dust electrocoagulation device
CN205462739U (en) Pipe electrostatic precipitators
CN107570324A (en) A kind of air purifier for being applicable computer room
CN106362880B (en) Bipolar charge-cyclone separator and technique for flue gas dedusting
CN108405184B (en) Industrial waste gas fine particulate matter removing device
CN205815928U (en) Franklinic electricity coalescer
CN105195320A (en) Constant-magnetism-enhancing dust removal device
CN100553737C (en) A kind of sound wave auxiliary composite bag type dust remover
CN104923403B (en) The devices and methods therefor of sound wave combined electric field action removing fine particle
CN206868433U (en) A kind of electric dust collector with sorting function
CN111068451B (en) Device and method for efficiently removing fine particulate matters through temperature and humidity regulation
CN206746199U (en) Double filter screen electrocoagulation fine particle cleaning equipment
CN110369133B (en) A dust collector is synthesized to sound electricity for belt transportation
CN111054168B (en) Device and method for efficiently removing multichannel fine particles
CN205868577U (en) Bipolar lotus that is used for flue gas dust removal whirlwind separator
CN106334625B (en) Bipolar charge magnetic for fume duct fly ash strengthens turbulent flow coalescence device
CN208660690U (en) The particulate matter coalescence device of bipolar charge and sound wave synergistic effect
CN107855220A (en) A kind of dust arrester suitable for computer room
CN213314149U (en) High-efficient dust collecting equipment is used to environmental protection engineering
CN203448182U (en) Electric dust remover
CN215027280U (en) Dust removing device

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
CP02 Change in the address of a patent holder
CP02 Change in the address of a patent holder

Address after: 221116 No. 1 University Road, copper mountain, Jiangsu, Xuzhou

Patentee after: CHINA University OF MINING AND TECHNOLOGY

Address before: 221116 Xuzhou University Road,, Jiangsu, China University of Mining and Technology

Patentee before: CHINA University OF MINING AND TECHNOLOGY

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

Granted publication date: 20170517