CN104043320B - A kind of photocatalysis plasma body is in conjunction with the method for ultrasonic Treatment room air pollution - Google Patents
A kind of photocatalysis plasma body is in conjunction with the method for ultrasonic Treatment room air pollution Download PDFInfo
- Publication number
- CN104043320B CN104043320B CN201410194933.9A CN201410194933A CN104043320B CN 104043320 B CN104043320 B CN 104043320B CN 201410194933 A CN201410194933 A CN 201410194933A CN 104043320 B CN104043320 B CN 104043320B
- Authority
- CN
- China
- Prior art keywords
- electrode
- vocs
- air
- reactor
- catalyst
- 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.)
- Expired - Fee Related
Links
- 238000000034 method Methods 0.000 title claims abstract description 21
- 238000003915 air pollution Methods 0.000 title claims abstract description 7
- 238000007146 photocatalysis Methods 0.000 title claims abstract description 7
- 230000001699 photocatalysis Effects 0.000 title claims abstract description 7
- 238000009210 therapy by ultrasound Methods 0.000 title claims abstract description 4
- 239000012855 volatile organic compound Substances 0.000 claims abstract description 16
- 239000003054 catalyst Substances 0.000 claims abstract description 14
- GWEVSGVZZGPLCZ-UHFFFAOYSA-N Titan oxide Chemical compound O=[Ti]=O GWEVSGVZZGPLCZ-UHFFFAOYSA-N 0.000 claims abstract description 10
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims abstract description 10
- 239000002250 absorbent Substances 0.000 claims abstract description 8
- 230000002745 absorbent Effects 0.000 claims abstract description 8
- 238000006243 chemical reaction Methods 0.000 claims abstract description 8
- 238000002604 ultrasonography Methods 0.000 claims abstract description 7
- 239000000945 filler Substances 0.000 claims abstract description 6
- 150000003254 radicals Chemical class 0.000 claims abstract description 6
- 229940070527 tourmaline Drugs 0.000 claims abstract description 6
- 229910052613 tourmaline Inorganic materials 0.000 claims abstract description 6
- 239000011032 tourmaline Substances 0.000 claims abstract description 6
- 238000012856 packing Methods 0.000 claims abstract description 5
- 239000006227 byproduct Substances 0.000 claims abstract description 4
- 150000002500 ions Chemical class 0.000 claims description 6
- 239000011941 photocatalyst Substances 0.000 claims description 6
- 230000000694 effects Effects 0.000 claims description 5
- NUJOXMJBOLGQSY-UHFFFAOYSA-N manganese dioxide Inorganic materials O=[Mn]=O NUJOXMJBOLGQSY-UHFFFAOYSA-N 0.000 claims description 5
- 239000000126 substance Substances 0.000 claims description 5
- 230000001590 oxidative effect Effects 0.000 claims description 4
- 230000015572 biosynthetic process Effects 0.000 claims description 3
- 239000008187 granular material Substances 0.000 claims description 3
- OGIDPMRJRNCKJF-UHFFFAOYSA-N titanium oxide Inorganic materials [Ti]=O OGIDPMRJRNCKJF-UHFFFAOYSA-N 0.000 claims description 3
- CURLTUGMZLYLDI-UHFFFAOYSA-N Carbon dioxide Chemical compound O=C=O CURLTUGMZLYLDI-UHFFFAOYSA-N 0.000 claims 2
- 229910002092 carbon dioxide Inorganic materials 0.000 claims 1
- 239000001569 carbon dioxide Substances 0.000 claims 1
- VUZPPFZMUPKLLV-UHFFFAOYSA-N methane;hydrate Chemical compound C.O VUZPPFZMUPKLLV-UHFFFAOYSA-N 0.000 claims 1
- SOQBVABWOPYFQZ-UHFFFAOYSA-N oxygen(2-);titanium(4+) Chemical compound [O-2].[O-2].[Ti+4] SOQBVABWOPYFQZ-UHFFFAOYSA-N 0.000 abstract description 3
- 239000004408 titanium dioxide Substances 0.000 abstract description 2
- 238000005265 energy consumption Methods 0.000 abstract 1
- 231100000252 nontoxic Toxicity 0.000 abstract 1
- 230000003000 nontoxic effect Effects 0.000 abstract 1
- 230000003287 optical effect Effects 0.000 abstract 1
- 239000013618 particulate matter Substances 0.000 description 6
- 238000005516 engineering process Methods 0.000 description 5
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 description 4
- 239000000356 contaminant Substances 0.000 description 4
- 239000002245 particle Substances 0.000 description 4
- 230000008569 process Effects 0.000 description 4
- 239000000779 smoke Substances 0.000 description 4
- 239000000428 dust Substances 0.000 description 3
- 239000000203 mixture Substances 0.000 description 3
- 238000007254 oxidation reaction Methods 0.000 description 3
- IJGRMHOSHXDMSA-UHFFFAOYSA-N Atomic nitrogen Chemical compound N#N IJGRMHOSHXDMSA-UHFFFAOYSA-N 0.000 description 2
- 150000001450 anions Chemical class 0.000 description 2
- 230000003197 catalytic effect Effects 0.000 description 2
- 238000006555 catalytic reaction Methods 0.000 description 2
- 239000003344 environmental pollutant Substances 0.000 description 2
- 239000000463 material Substances 0.000 description 2
- 230000003647 oxidation Effects 0.000 description 2
- 231100000719 pollutant Toxicity 0.000 description 2
- 238000004062 sedimentation Methods 0.000 description 2
- 238000001179 sorption measurement Methods 0.000 description 2
- 206010020751 Hypersensitivity Diseases 0.000 description 1
- CBENFWSGALASAD-UHFFFAOYSA-N Ozone Chemical compound [O-][O+]=O CBENFWSGALASAD-UHFFFAOYSA-N 0.000 description 1
- 238000010521 absorption reaction Methods 0.000 description 1
- 230000009471 action Effects 0.000 description 1
- 239000000809 air pollutant Substances 0.000 description 1
- 231100001243 air pollutant Toxicity 0.000 description 1
- 208000026935 allergic disease Diseases 0.000 description 1
- 230000007815 allergy Effects 0.000 description 1
- 238000013459 approach Methods 0.000 description 1
- 208000006673 asthma Diseases 0.000 description 1
- 230000015556 catabolic process Effects 0.000 description 1
- 230000008859 change Effects 0.000 description 1
- 239000011248 coating agent Substances 0.000 description 1
- 238000000576 coating method Methods 0.000 description 1
- 238000000354 decomposition reaction Methods 0.000 description 1
- 238000006731 degradation reaction Methods 0.000 description 1
- 238000007599 discharging Methods 0.000 description 1
- 201000010099 disease Diseases 0.000 description 1
- 208000037265 diseases, disorders, signs and symptoms Diseases 0.000 description 1
- 230000005684 electric field Effects 0.000 description 1
- 230000003628 erosive effect Effects 0.000 description 1
- 239000003574 free electron Substances 0.000 description 1
- 239000007789 gas Substances 0.000 description 1
- 231100001261 hazardous Toxicity 0.000 description 1
- 230000036541 health Effects 0.000 description 1
- -1 hydroxyl radical free radical Chemical class 0.000 description 1
- 230000008676 import Effects 0.000 description 1
- 210000004072 lung Anatomy 0.000 description 1
- 229910021645 metal ion Inorganic materials 0.000 description 1
- 244000005700 microbiome Species 0.000 description 1
- 239000004531 microgranule Substances 0.000 description 1
- 229910052757 nitrogen Inorganic materials 0.000 description 1
- 239000005416 organic matter Substances 0.000 description 1
- 239000003960 organic solvent Substances 0.000 description 1
- 239000007800 oxidant agent Substances 0.000 description 1
- 230000002085 persistent effect Effects 0.000 description 1
- 238000013033 photocatalytic degradation reaction Methods 0.000 description 1
- 238000012545 processing Methods 0.000 description 1
- 230000000717 retained effect Effects 0.000 description 1
- 238000007086 side reaction Methods 0.000 description 1
- 230000003068 static effect Effects 0.000 description 1
- 238000013517 stratification Methods 0.000 description 1
- 230000001988 toxicity Effects 0.000 description 1
- 231100000419 toxicity Toxicity 0.000 description 1
Classifications
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02A—TECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
- Y02A50/00—TECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE in human health protection, e.g. against extreme weather
- Y02A50/20—Air quality improvement or preservation, e.g. vehicle emission control or emission reduction by using catalytic converters
Landscapes
- Exhaust Gas Treatment By Means Of Catalyst (AREA)
- Catalysts (AREA)
Abstract
The invention discloses a kind of photocatalysis plasma body method in conjunction with ultrasonic Treatment room air pollution.Comprise the following steps: 1, use plasma discharge reactor having to produce stream plasma free radical, highfield and ultraviolet light；2, PM2.5 is adsorbed by highfield；3, reacted with the VOCs in air by plasma free radical so that it is innoxious；4, the VOCs of non-complete reaction is reacted further by titanium dioxide optical catalyst；5, by-product NOx, O that reaction produces3Decomposed by safe catalyst；6, water or non-toxic organic thing absorbent are sufficiently mixed by ultrasound reactor and tail gas, fully react in packing area, remainder particulate thing and VOCs are stayed in organic absorbent；7, packing area uses tourmaline load nano-titanium dioxide filler.This method has low energy consumption, takes up an area advantage little, that noise is little, applied widely, safe and reliable to operation.
Description
Technical field
The present invention relates to a kind of method that nano-photo catalytic corona plasma processes indoor air pollutants in conjunction with ultrasound wave Organic substance absorption techniques, belong to air Treatment process field.
Background technology
Along with the air pollution day by day increased the weight of, the degree that haze occurs is more and more higher, and frequency is increasingly faster, and the persistent period is more and more longer, and PM2.5, as the important indicator of haze, directly affects living safety and the quality of people.PM2.5 refers to that in air, the particulate matter of diameter≤2.5 micron is also referred to as entering lung particulate matter.Air quality and visibility etc. are had a significant impact by it.Health, owing to particle diameter is little, specific surface area big, easily adhere to various hazardous contaminants, can be directly entered in human body alveolar, is therefore produced serious threat by PM2.5.Owing to PM2.5 particle diameter is little, it is difficult to from sedimentation or is fallen by rain drop erosion, being therefore difficult in atmosphere be removed.
One of major reason that volatile organic matter VOCs also haze produces, the VOCs in air produces reaction under the irradiation of sunlight and forms secondary pollution generation photochemical fog, has strong impulse, toxicity, carcinogenecity.
Present stage can effectively process the method for PM2.5 and only have 2 kinds in indoor, and one is to use HEPA to be filtered；Another kind is to utilize anion to make PM2.5 particulate matter form heavy ion sedimentation.But both approaches is respectively arranged with drawback.
1, using HEPA to be filtered, it is necessary to frequently to change HEPA, therefore cost of use is expensive, and HEPA changes and filter opening can be caused not in time to block, and the HEPA simultaneously polluted can grow substantial amounts of microorganism, becomes new polluter.
2, use anion to remove PM2.5, PM2.5 granule not eliminate from environment, but be adsorbed on indoor body surface in a large number, cause house dust to increase, it is easy to cause the other diseases such as allergy, asthma.
The VOCs treatment technology that present stage can use in indoor environment only has activated carbon adsorption and photocatalysis technology, during long-time use, adsorption effect of activated carbon in water is poor, photocatalysis technology activates generation free electron and electron hole due to catalyst mainly by ultraviolet light, and therefore degradation efficiency is very low.
Summary of the invention
It is an object of the invention to propose a kind of air pollution treatment technology suitable in indoor environment.By using DC high voltage electric field by PM2.5 particulate collection on electrode, the free radical that high pressure streamer-discahrge produces is used to process indoor VOCs, and carry out photocatalytic degradation by the ultraviolet light produced that discharges, mix with pollutant after water or Organic substance absorbent being atomized by ultrasound wave, fully react at tourmaline load nano-titanium dioxide filling surface, utilize the static behaviour that tourmaline has, fully adsorb contaminant remaining, and carry out catalytic oxidation.By-product NOx and the O of exoelectrical reaction3Pass through MnO2Safe catalyst is removed.This method overcomes prior art cost of use high, easily causes secondary pollution, the problem of poor processing effect.
A kind of administering method of room air pollution, it is characterized in that comprising the following steps: blower fan introduces air in discharge reactor, the module composition that discharge reactor is made up of bipolar needle electrode and nano titanic oxide catalyst net, air passes through MnO in discharge reactor outlet2Safe catalyst, then with ultrasound wave formed water smoke mix after entrance filler in fully react, eventually pass back to indoor.
(1)Use high direct voltage alternating expression bipolar needle electrode streamer-discahrge reactor, contaminated air is passed in discharge reactor, regulate voltage and make positive pole form stable streamer.
(2)The high energy electron bombardment air molecule that electrion produces makes gas band electric forming plasma, so that contaminant particle (particularly PM2.5 granule) is combined formation heavy ion with plasma, heavy ion moves to electrode under the effect of highfield, it is attracted on electrode, needle plate electrode is owing to discharging at pin end, it is possible to avoid the impact of electrode dust stratification.
(3)Air forms plasma, hydroxyl radical free radical and ozone etc. after being bombarded by high energy electron, and VOCs can react with these materials and be eliminated.
(4)High pressure streamer-discahrge can produce strong ultraviolet light, and VOCs is subject to irradiation under ultraviolet ray after being adsorbed to photocatalyst surface, and photocatalyst surface forms electron hole, has strong oxidizing property, it is possible to oxidation Decomposition VOCs.
(5)Owing to air existing substantial amounts of nitrogen, NO during electric discharge, also can be formed2And O3, these by-products pass through MnO2Safe catalyst eliminates.
(6)Remain untreated fall PM2.5 particulate matter and after the organic solvent water smoke that produces with ultrasound reactor of VOCs mixes, enter packing area reaction.Tourmaline appendix nano titanium oxide filler has very strong surface electrostatic, and adsorptivity is strong, and therefore contaminant remaining and water smoke are adsorbed to filling surface and fully react.
Accompanying drawing explanation
Fig. 1 is discharge reactor electrode group module front view.
Fig. 2 is discharge reactor electrode group module isometric view.
Detailed description of the invention
Air introduces in streamer-discahrge reactor by blower fan, and reactor uses high-voltage DC power supply, and both positive and negative polarity is needle plate electrode, and the pin of both positive and negative polarity is staggered.Needle point 3 is 2 ~ 5cm to the distance of another pole pole plate 1, needle point 3 spacing 2 ~ 4cm on same electrode, and voltage swing is as the criterion for making positive pole generation streamer-discahrge.
Discharge reactor has modularity, and each module is made up of multi-group electrode plate, and what wherein pin number was more is positive plate 1, and pin number is less for negative plate 2, and module imports and exports two ends nano titanic oxide catalyst net 4.
When air is by discharge reactor, air molecule forms plasma after being bombarded by high energy electron, these high energy particle positively chargeds or negative point, the particulate matter that can attract opposed polarity forms heavy ion, PM2.5 particulate matter volume is made to increase, electric charge strengthens, and the move under influence at highfield settles down to other end electrode.
Having layer of titanium dioxide coating on the plate of needle plate electrode 1,2, it is possible to the ultraviolet light absorbing exoelectrical reaction generation carries out photocatalysis oxidation reaction, importing and exporting at each group of electrode all has one layer of nano titanium dioxide photocatalyst net.
VOCs can be subject to exoelectrical reaction and produce-OH base ,-O base, O after entering reactor3Deng the action breaks of strong oxidizer, simultaneously because the ultraviolet exciting light catalyst that electric discharge produces, forming electron hole on catalyst gauze, electron hole has strong oxidizing property, it is possible to decompose VOCs.
Owing to air there is also N2And NOx, therefore also can produce side reaction
3O2(high pressure) → 2O3
N2+O2→2NO
2NO+O2→2NO2
NO+O3→NO2+O2
O3And NO2It it is all harmful material.
When air passes through MnO in discharge reactor exit2Safe catalysis net, MnO2Can by O3It is converted into O2, by NO2It is converted into NO3 -。
When air is mixed by the Organic substance absorbent water smoke produced with ultrasound reactor after safe catalysis net, enter packing area, tourmaline appendix nano titanium oxide filler has very strong surface electrostatic meeting adsorbing metal ions, charged dust etc., therefore pollutant and absorbent fully react at filling surface, make remaining PM2.5 microgranule and VOCs are retained down by filler after being absorbed by absorbent.
Claims (8)
1. a photocatalysis plasma body is in conjunction with the method for ultrasonic Treatment room air pollution, it is characterised in that: comprise the following steps,
(1) DC bipolar needle electrode discharge of plasma in low temperature reactor is utilized to produce plasma free radical, highfield and ultraviolet light；
(2) high energy electron when utilizing discharge reactor to produce streamer bombards air molecule, makes air molecule ionize, forms plasma, also can form substantial amounts of-OH, H simultaneously2O2、O3Strong free radical；
(3) strong oxidizing property that the strong free radical that electric discharge produces has is utilized to decompose VOCs；
(4) ionized air and PM2.5 granule can attract each other formation heavy ion, and heavy ion is finally caught by electrode to electrode movement under highfield effect, thus separating from air；
(5) discharge reactor can produce ultraviolet light while producing streamer, and ultraviolet light can activate photocatalyst, forms electron hole, and the electron hole of formation has strong oxidizing property；
(6), after a part of VOCs is adsorbed by nano-photocatalyst, harmless carbon dioxide and water it are degraded on a catalyst；
(7) exoelectrical reaction also can form by-product NOx and O3, at MnO2It is broken off under the effect of safe catalyst；
(8) ultrasound reactor mixes with tail gas after water or Organic substance absorbent being atomized, and jointly enters packing area, and after filling surface is sufficiently mixed dissolving, filled retaining is separated, and finally makes outlet emission compliance.
2. method according to claim 1, it is characterised in that discharge reactor uses DC high-voltage power supply, and positive source connects anode plate, power cathode connects negative plates, and pole plate is needle plate electrode, and positive and negative needle electrode is staggered.
3. method according to claim 1, it is characterised in that supply voltage just makes positive pole form streamer-discahrge, the battery lead plate that just extremely pin number is more.
4. method according to claim 1, it is characterised in that be coated with nano titanic oxide catalyst on both positive and negative polarity battery lead plate.
5. method according to claim 1, it is characterised in that discharge reactor is made up of several equirotal electrode group modules, modular electrode group is by several staggered to positive and negative needle plate electrode, and electrode group two ends are equipped with photocatalyst net.
6. method according to claim 1, it is characterised in that discharge reactor exports equipped with MnO2Catalyst.
7. method according to claim 1, it is characterised in that ultrasonic atomized water or mix with air after Organic substance absorbent.
8. method according to claim 1, it is characterised in that the filler of use is granular tourmaline appendix nano titanium oxide.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN201410194933.9A CN104043320B (en) | 2014-05-11 | 2014-05-11 | A kind of photocatalysis plasma body is in conjunction with the method for ultrasonic Treatment room air pollution |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN201410194933.9A CN104043320B (en) | 2014-05-11 | 2014-05-11 | A kind of photocatalysis plasma body is in conjunction with the method for ultrasonic Treatment room air pollution |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| CN104043320A CN104043320A (en) | 2014-09-17 |
| CN104043320B true CN104043320B (en) | 2016-07-06 |
Family
ID=51497013
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| CN201410194933.9A Expired - Fee Related CN104043320B (en) | 2014-05-11 | 2014-05-11 | A kind of photocatalysis plasma body is in conjunction with the method for ultrasonic Treatment room air pollution |
Country Status (1)
| Country | Link |
|---|---|
| CN (1) | CN104043320B (en) |
Families Citing this family (14)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN103968466B (en) * | 2014-05-20 | 2017-01-18 | 郑巍 | Indoor air processing technology and device |
| CN104923060B (en) * | 2015-04-21 | 2017-05-03 | 江苏大学 | VOCs removing method based on free radical advanced oxidation |
| CN105130046B (en) * | 2015-08-13 | 2017-06-16 | 南通河海大学海洋与近海工程研究院 | Plasma and ultrasound and the tandem type water treatment facilities of catalytic association |
| CN105233641B (en) * | 2015-10-21 | 2018-01-02 | 中国科学院北京综合研究中心 | The method and device of bioxin caused by incineration of waste and mercury deep purifying |
| CN107149857A (en) * | 2016-03-02 | 2017-09-12 | 北京大学 | Multi-layer planar corona low temperature plasma air cleaning unit |
| CN106051918B (en) * | 2016-07-05 | 2022-05-20 | 北京航天爱锐科技有限责任公司 | Plasma air purification device |
| CN106422699A (en) * | 2016-08-29 | 2017-02-22 | 浙江工业大学 | Method and device for coupling and biologically purifying VOCs under optical/thermal double-driving catalysis |
| CN106890552A (en) * | 2017-03-13 | 2017-06-27 | 苏州盟力环境科技有限公司 | A kind of plasma gas processing unit |
| CN107174879A (en) * | 2017-04-18 | 2017-09-19 | 上海英宇环保科技有限公司 | A kind of plasma air purifier |
| CN109882877B (en) * | 2018-04-14 | 2020-04-28 | 青岛科技大学 | Flue gas waste heat utilization and automatic pollutant control system |
| CN109882878B (en) * | 2018-04-14 | 2020-04-28 | 青岛科技大学 | Intelligent flue gas waste heat utilization and flue gas pollutant treatment system thereof |
| CN111111442A (en) * | 2019-12-30 | 2020-05-08 | 长安大学 | A kind of long afterglow automobile exhaust purification coating and preparation method and application thereof |
| CN112413784A (en) * | 2020-11-27 | 2021-02-26 | 上海交通大学 | Portable multifunctional air purification method and device |
| CN117628629B (en) * | 2024-01-24 | 2024-04-02 | 泉州市奔腾科技有限责任公司 | Air purifying equipment |
Family Cites Families (5)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JP2003305336A (en) * | 2002-04-15 | 2003-10-28 | Jfe Engineering Kk | Adsorbent packed bed equipment |
| JP2008194670A (en) * | 2007-01-15 | 2008-08-28 | Yamatake Corp | Gas processing equipment |
| CN101367031A (en) * | 2008-09-12 | 2009-02-18 | 江苏大学 | A device and method for generating hydroxyl radicals by ultrasonic waves in cooperation with strong ionization discharge |
| CN101934190B (en) * | 2010-09-14 | 2012-10-17 | 山东派力迪环保工程有限公司 | Matrix type dielectric barrier discharge plasma peculiar smell gas treatment device |
| CN201940160U (en) * | 2010-11-29 | 2011-08-24 | 江苏紫光吉地达环境科技股份有限公司 | Plasma wind-guiding plate type waste-gas purifying device |
-
2014
- 2014-05-11 CN CN201410194933.9A patent/CN104043320B/en not_active Expired - Fee Related
Also Published As
| Publication number | Publication date |
|---|---|
| CN104043320A (en) | 2014-09-17 |
Similar Documents
| Publication | Publication Date | Title |
|---|---|---|
| CN104043320B (en) | A kind of photocatalysis plasma body is in conjunction with the method for ultrasonic Treatment room air pollution | |
| CN203364250U (en) | Filtering dedusting disinfection apparatus of indoor air purifier | |
| CN103586131A (en) | Device and method for purifying indoor air through electrostatic atomization | |
| CN104501311A (en) | Indoor air purifying method and indoor air purifying device | |
| CN204214007U (en) | Cooking fume remover | |
| CN2778371Y (en) | Plasma and light catalyzing combined air purifier device | |
| CN105698293B (en) | A kind of Multifunctional air clarifying device | |
| CN103830989A (en) | Method for treating haze and indoor air pollution by using tourmaline honeycomb body | |
| CN202893503U (en) | Indoor air purification device by electrostatic atomization | |
| CN108525482A (en) | A kind of device and method of high-voltage pulse dielectric barrier discharge combination electrostatic microjet atomization removing VOCs | |
| CN103742984B (en) | The micro-water curtain air purification method of magnetoelectricity and device | |
| CN104307358A (en) | Odor purification device | |
| CN105233611A (en) | Electric field and corona combined photocatalytic air purifier | |
| CN105772221B (en) | A kind of Multifunctional air clarifying device | |
| CN203276733U (en) | Video display equipment with one or more air disinfection and purification technologies | |
| CN104553685A (en) | Vehicle-mounted safe driving instrument with built-in purifying sterilizing system | |
| CN103968466B (en) | Indoor air processing technology and device | |
| CN203298403U (en) | Air purifier | |
| CN104494398A (en) | Navigation system and device capable of purifying in-car air | |
| CN105709597B (en) | A kind of the flue gas ash removal mercury removal device and its processing method of plasma reactor joint membrane bag filter | |
| CN105387525A (en) | Air purifier | |
| CN203389490U (en) | Asphalt smoke-gas treatment system | |
| CN1597068A (en) | Method of cleaning air pollutant using synergistic action of streamer discharge and photo catalysis | |
| CN203797809U (en) | Industrial air purifier | |
| CN201421147Y (en) | Disinfection and purification 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 | ||
| CB03 | Change of inventor or designer information |
Inventor after: Zheng Wei Inventor after: Zhao Ning Inventor after: Xiao Ling Inventor after: Li Changguo Inventor before: Zheng Wei Inventor before: Xiao Ling Inventor before: Li Changguo |
|
| COR | Change of bibliographic data | ||
| C14 | Grant of patent or utility model | ||
| GR01 | Patent grant | ||
| 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: 20160706 |