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 PDFInfo
- 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
Links
Classifications
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B03—SEPARATION OF SOLID MATERIALS USING LIQUIDS OR USING PNEUMATIC TABLES OR JIGS; MAGNETIC OR ELECTROSTATIC SEPARATION OF SOLID MATERIALS FROM SOLID MATERIALS OR FLUIDS; SEPARATION BY HIGH-VOLTAGE ELECTRIC FIELDS
- B03C—MAGNETIC OR ELECTROSTATIC SEPARATION OF SOLID MATERIALS FROM SOLID MATERIALS OR FLUIDS; SEPARATION BY HIGH-VOLTAGE ELECTRIC FIELDS
- B03C3/00—Separating dispersed particles from gases or vapour, e.g. air, by electrostatic effect
- B03C3/34—Constructional details or accessories or operation thereof
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B03—SEPARATION OF SOLID MATERIALS USING LIQUIDS OR USING PNEUMATIC TABLES OR JIGS; MAGNETIC OR ELECTROSTATIC SEPARATION OF SOLID MATERIALS FROM SOLID MATERIALS OR FLUIDS; SEPARATION BY HIGH-VOLTAGE ELECTRIC FIELDS
- B03C—MAGNETIC OR ELECTROSTATIC SEPARATION OF SOLID MATERIALS FROM SOLID MATERIALS OR FLUIDS; SEPARATION BY HIGH-VOLTAGE ELECTRIC FIELDS
- B03C3/00—Separating dispersed particles from gases or vapour, e.g. air, by electrostatic effect
- B03C3/01—Pretreatment 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
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.
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)
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)
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 |
-
2016
- 2016-05-23 CN CN201610341415.4A patent/CN105921276B/en not_active Expired - Fee Related
Patent Citations (7)
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)
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 |