CN2788888Y - Electric-bag combined dust cleaner - Google Patents
Electric-bag combined dust cleaner Download PDFInfo
- Publication number
- CN2788888Y CN2788888Y CN200520078762.XU CN200520078762U CN2788888Y CN 2788888 Y CN2788888 Y CN 2788888Y CN 200520078762 U CN200520078762 U CN 200520078762U CN 2788888 Y CN2788888 Y CN 2788888Y
- Authority
- CN
- China
- Prior art keywords
- dust
- electric
- bag
- unit
- utility
- 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
- 239000000428 dust Substances 0.000 title claims abstract description 67
- UGFAIRIUMAVXCW-UHFFFAOYSA-N Carbon monoxide Chemical compound [O+]#[C-] UGFAIRIUMAVXCW-UHFFFAOYSA-N 0.000 claims description 13
- 239000003546 flue gas Substances 0.000 claims description 13
- 150000001875 compounds Chemical class 0.000 claims description 7
- 239000002245 particle Substances 0.000 abstract description 11
- 238000000034 method Methods 0.000 abstract description 7
- 238000001914 filtration Methods 0.000 abstract description 6
- 239000000463 material Substances 0.000 abstract description 3
- 238000005265 energy consumption Methods 0.000 abstract description 2
- 238000001556 precipitation Methods 0.000 description 14
- 230000000694 effects Effects 0.000 description 11
- 230000005684 electric field Effects 0.000 description 6
- 230000008676 import Effects 0.000 description 6
- AXCZMVOFGPJBDE-UHFFFAOYSA-L calcium dihydroxide Chemical compound [OH-].[OH-].[Ca+2] AXCZMVOFGPJBDE-UHFFFAOYSA-L 0.000 description 5
- 229910001861 calcium hydroxide Inorganic materials 0.000 description 5
- 239000000920 calcium hydroxide Substances 0.000 description 5
- 238000010410 dusting Methods 0.000 description 5
- 238000005516 engineering process Methods 0.000 description 4
- 239000007789 gas Substances 0.000 description 4
- 239000000843 powder Substances 0.000 description 4
- 238000004140 cleaning Methods 0.000 description 3
- RAHZWNYVWXNFOC-UHFFFAOYSA-N Sulphur dioxide Chemical compound O=S=O RAHZWNYVWXNFOC-UHFFFAOYSA-N 0.000 description 2
- 230000005611 electricity Effects 0.000 description 2
- 239000003500 flue dust Substances 0.000 description 2
- 230000035484 reaction time Effects 0.000 description 2
- 230000035939 shock Effects 0.000 description 2
- 239000007921 spray Substances 0.000 description 2
- 238000013517 stratification Methods 0.000 description 2
- 235000008733 Citrus aurantifolia Nutrition 0.000 description 1
- 235000011941 Tilia x europaea Nutrition 0.000 description 1
- 150000001450 anions Chemical class 0.000 description 1
- 238000013459 approach Methods 0.000 description 1
- 230000009286 beneficial effect Effects 0.000 description 1
- 238000004891 communication Methods 0.000 description 1
- 238000010276 construction Methods 0.000 description 1
- 230000007812 deficiency Effects 0.000 description 1
- 230000003111 delayed effect Effects 0.000 description 1
- 238000006477 desulfuration reaction Methods 0.000 description 1
- 230000023556 desulfurization Effects 0.000 description 1
- 238000010586 diagram Methods 0.000 description 1
- 230000005686 electrostatic field Effects 0.000 description 1
- 238000002474 experimental method Methods 0.000 description 1
- 239000003517 fume Substances 0.000 description 1
- 239000008187 granular material Substances 0.000 description 1
- 229910001385 heavy metal Inorganic materials 0.000 description 1
- 238000009413 insulation Methods 0.000 description 1
- 239000004571 lime Substances 0.000 description 1
- 238000009428 plumbing Methods 0.000 description 1
- 229910052573 porcelain Inorganic materials 0.000 description 1
- 238000010926 purge Methods 0.000 description 1
- 238000000746 purification Methods 0.000 description 1
- 239000000779 smoke Substances 0.000 description 1
- 230000003068 static effect Effects 0.000 description 1
- 238000005406 washing Methods 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
- Y02A50/2351—Atmospheric particulate matter [PM], e.g. carbon smoke microparticles, smog, aerosol particles, dust
Landscapes
- Filtering Of Dispersed Particles In Gases (AREA)
Abstract
The utility model relates to an electric bag combined type dust remover which comprises an electric dust removing unit and a bag type dust collecting unit, wherein a perforated plate (11) is arranged between the electric dust removing unit and the bag type dust collecting unit, and both sides of the perforated plate are provided with flow guiding channels (16). An inlet of the dust remover of the utility model is provided with an inlet horn (6), the interior of which is provided with two layers or three layers of air flow distribution plates (5). The utility model effectively combines the advantages of two traditional methods, the dust removing efficiency for microfine particles is high, the circulation resistance of the air flow of the dust remover is small, the operation energy consumption is low, and the service life of the filtering material is long.
Description
Technical field
The utility model relates to a kind of deduster, relates in particular to a kind of electricity-bag compound type dust remover.
Background technology
At present, efficient nonaqueous dust cleaner mainly contains two kinds, and a kind of is electric cleaner, and a kind of is sack cleaner.The basic principle of electric cleaner is to utilize electrion to make dust in flue gas charged in the deduster electric field, and charged dust moves under the effect of electric field force and attached to the dust collecting pole plate surface, thereby reaches the purpose of dedusting.The electric cleaner running resistance is little, however since not high to the particle efficiency of dust collection of minuteness particle and high specific resistance, cause the total efficiency of dust collection of deduster to descend, and one time investment cost increases.Sack cleaner is based on the principle of filtering, and is higher to the minuteness particle efficiency of dust collection, but the deduster running resistance is bigger, and the while washes away because of particle or the red-hot particle of high temperature influences the lost of life that makes filtering material.
Summary of the invention
For overcoming the deficiencies in the prior art, the purpose of this utility model provide a kind of purification efficiency height, running resistance low, remove be rich in heavy metal the minuteness particle effect obviously, can efficiently remove the electricity-bag compound type dust remover of industrial fumes.
The imagination of the utility model technical solution problem is:
1, the deduster intake method adopts straight-through air inlet.The structure of straight-through air inlet comprises: gas approach loudspeaker, airflow-distribution board, deflector.
2, deduster is divided into along its length two dust removing units.First module is the electric precipitation unit, principle is identical with the electric cleaner principle, dusty gas is being undertaken by the high-voltage electrostatic field in the process of ionization, make dust charged, charged dust in the effect deposit of electric field force on dust collecting pole plate, adopt the method for mechanical vibrator to make the grit on discharge electrode and dust collecting pole plate surface fall into ash bucket, reach the dedusting purpose.Deduster Unit second is the bag-type dusting unit, and dust-cleaning principle is identical with sack cleaner.Flue gas enters after the bag-type dusting unit, flows to the filter bag inboard by the outside, and during space by filter bag, dust is delayed at the outer surface of filter bag, forms dust layer.Sack cleaner adopts the purge mode of pulse jet, the pulse jet process sprays into filter bag with compressed air in the of short duration time, induce the air that is several times as much as jet simultaneously, filter bag opening produces rapid expansion and impact shock to the bottom, the dust on filter bag surface falls into ash bucket owing to inertia comes off from filter bag.
3, the combination of electric precipitation unit and bag-type dusting unit.Flue gas enters a bag dust removing units after by the electric precipitation unit.Flue gas directly do not enter a bag dust removing units, avoided flue dust to directly the washing away of filter bag, and life-span of the filter bag prolongs.Between electric precipitation unit and bag dust removing units, porous plate and flow-guiding channel are set, ash-laden gas by porous plate and flow-guiding channel after, can enter predetermined space according to a certain percentage, evenly carry and be assigned to each filter bag unit, do not influence efficiency of dust collection, running resistance reduces, and has avoided flue dust to wash away the damage filter bag, prolongs the service life of filter bag.Through repeatedly experiment, the ratio that the flue gas flow by both sides flow-guiding channel, porous plate and porous plate bottom accounts for total flow is controlled to be 15%, 15%, 30%, 40% respectively.
When dust-contained airflow enters into deduster, through the previous section electric precipitation, can remove most dust earlier, the dust of not removing mainly is a minuteness particle, and concentration is not high, at this moment passes through the bag-type dust unit again, can reach good dust removing effects.
For solving the problems of the technologies described above, the technical scheme that the utility model technical solution problem is adopted is:
Comprise electric cleaner, sack cleaner, a porous plate 11 is set between described electric cleaner and the bag collector, the both sides of porous plate are provided with flow-guiding channel 16.
The flue gas of the flow-guiding channel 16 of described both sides is controlled to be 15% respectively, is 40% from the flow-control of porous plate bottom, and the flue gas by porous plate is 30%.
Described deduster import department is provided with import loudspeaker 6, is equipped with two-layer in these import loudspeaker (6) or three layers of airflow-distribution board 5.
The beneficial effects of the utility model are, straight-through air inlet electricity-bag compound type dust remover effectively combines the advantage of two kinds of methods of tradition, minuteness particle efficiency of dust collection height, and deduster airflow resistance is little, and operation energy consumption is low, the filtering material long service life.
Description of drawings
The utility model is described in further detail below in conjunction with drawings and Examples:
Fig. 1 is the utility model structure chart;
Fig. 2 is the C-C cutaway view of Fig. 1;
Fig. 3 is the D-D cutaway view (perforated plate construction figure) of Fig. 1
Fig. 4 is the schematic diagram of the utility model desulfurization embodiment.
The specific embodiment
As depicted in figs. 1 and 2, the body of deduster is mainly by import loudspeaker 6, electric precipitation unit, bag-type dusting unit, and three parts are formed.Airflow-distribution board 5 is housed in the import loudspeaker.First module is the electric precipitation unit in two unit, mainly is made of corona wire 7, dust collector pole 15 plates, rapping apparatus 4, ash bucket 2 and incubator 10.Corona wire 7 is fixed in the cathode frame 9, is suspended on the insulation porcelain knob 8, and connects high-tension electricity, dust collector pole 15 plate earthings.When dust stratification acquires a certain degree, start rapping apparatus 4, carry out vibration dust-cleaning.Unit second is the bag-type dusting unit, mainly is made of filter bag and support frame 13 thereof, pulse valve 12, pulse tube 14.Filter type is an outside filtering type, arrives to a certain degree when ash is long-pending, and unbalanced pulse valve 12 carries out pulse dust cleaning.
After flue gas entered deduster, at first by import loudspeaker 6, under the effect of airflow-distribution board 5, air-flow distributed more even, enters the electric precipitation unit.Because corona wire 7 connects high-tension electricity, produces a large amount of electronics and anion, makes dust in flue gas charged, charged grit moves to dust collector pole 15 under the effect of electric field force, and is deposited on the dust collecting pole plate 15.Make grit fall into ash bucket 2 by rapping apparatus 4 vibration corona wires 7 and dust collector pole 15, reach the dedusting purpose.The electric precipitation unit carries out dedusting, and the electric precipitation unit has only an electric field, and dust-collecting efficiency is more than 70%, and remaining dust granules is thin, and is more higher relatively than resistance, collects relatively difficulty.This a part of dust electric field unit in front enters the pocket type unit that gathers dust through porous plate 11 and flow-guiding channel 16 after fully charged, because dust load is low and static reinforced effect, under the effect of filtering, dust deposit is on the surface of filter bag 13, when the pressure of filter bag 13 acquires a certain degree, rapid unbalanced pulse valve 12, compressed air is in abrupt release, in filter bag 13, spray, filter bag 13 outwards sharply expands therefore and rapidly, produce an impact shock, the dust on filter bag 13 surfaces falls into ash bucket 2 owing to inertia comes off from filter bag.Dust stratification in ash bucket 2 is discharged by unloading valve 1.
As shown in Figure 3, in porous plate 11 structure charts, gather dust and add a porous plate 11 between the unit in electric precipitation unit and bag, bar flow-guiding channel 16 is reserved in the both sides of porous plate, when flue gas enters dust removing units, under the effect of porous plate, air communication is crossed porous plate and two flow-guiding channels 16 and porous plate bottom and is entered a bag dust removing units.
Embodiment:
As shown in Figure 3, enter deduster 4 behind boiler 1 tail flue gas and calcium hydroxide powder process economizer 2 and the air preheater 3, at first carry out electric precipitation in the electric precipitation unit, the particle of not removing also passes through fully charged, utilize the dedusting of bag dust removing units again, effect is fine.The particle that the electric precipitation unit is collected is recoverable to again and utilizes because the reaction time is short.The calcium hydroxide powder that the calcium hydroxide powder of receiving is delivered in humidification slaking blender 9 and the calcium hydroxide storehouse 10 by conveying worm 8 mixes, and adds the boiler plumbing again, forms lime white, enters into boiler smoke through feeder 12 and reacts with sulfur dioxide.Long owing to the reaction time at the dust that the bag dust removing units is collected, the calcium hydroxide powder loses activity, and therefore, can directly discharge.Purified gas is discharged by boiler induced-draft fan 5, chimney 6.Electricity-bag complex dust collector is the nucleus equipment in the technology in the whole technology.
Claims (3)
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN200520078762.XU CN2788888Y (en) | 2005-05-12 | 2005-05-12 | Electric-bag combined dust cleaner |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN200520078762.XU CN2788888Y (en) | 2005-05-12 | 2005-05-12 | Electric-bag combined dust cleaner |
Publications (1)
| Publication Number | Publication Date |
|---|---|
| CN2788888Y true CN2788888Y (en) | 2006-06-21 |
Family
ID=36789228
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| CN200520078762.XU Expired - Fee Related CN2788888Y (en) | 2005-05-12 | 2005-05-12 | Electric-bag combined dust cleaner |
Country Status (1)
| Country | Link |
|---|---|
| CN (1) | CN2788888Y (en) |
Cited By (8)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN101829470A (en) * | 2010-05-15 | 2010-09-15 | 山西省电力公司电力建设四公司 | Construction technique of electric bag compound type dust remover |
| CN102430309A (en) * | 2011-10-23 | 2012-05-02 | 中冶焦耐(大连)工程技术有限公司 | A fine particle coal recovery device |
| CN102430310A (en) * | 2011-10-23 | 2012-05-02 | 中冶焦耐(大连)工程技术有限公司 | A method for recovering fine particle coal |
| CN102133497B (en) * | 2010-01-27 | 2013-01-23 | 张政 | Micro-electricity combined dust collector used for tail of belt type conveyer |
| CN105148670A (en) * | 2015-09-17 | 2015-12-16 | 合肥中亚环保科技有限公司 | Bag-wet combined electrical dust remover |
| CN112156600A (en) * | 2020-09-19 | 2021-01-01 | 昆明理工大学 | Method and device for preventing pipeline for conveying yellow phosphorus furnace gas from being blocked and removing dust |
| CN112170010A (en) * | 2020-10-15 | 2021-01-05 | 艾尼科环保技术(安徽)有限公司 | Novel electrostatic precipitator import loudspeaker |
| CN118417057A (en) * | 2024-07-02 | 2024-08-02 | 山西省安装集团股份有限公司 | Dust removing device for heat source plant |
-
2005
- 2005-05-12 CN CN200520078762.XU patent/CN2788888Y/en not_active Expired - Fee Related
Cited By (10)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN102133497B (en) * | 2010-01-27 | 2013-01-23 | 张政 | Micro-electricity combined dust collector used for tail of belt type conveyer |
| CN101829470A (en) * | 2010-05-15 | 2010-09-15 | 山西省电力公司电力建设四公司 | Construction technique of electric bag compound type dust remover |
| CN101829470B (en) * | 2010-05-15 | 2011-11-23 | 山西省电力公司电力建设四公司 | Construction technique of electric bag compound type dust remover |
| CN102430309A (en) * | 2011-10-23 | 2012-05-02 | 中冶焦耐(大连)工程技术有限公司 | A fine particle coal recovery device |
| CN102430310A (en) * | 2011-10-23 | 2012-05-02 | 中冶焦耐(大连)工程技术有限公司 | A method for recovering fine particle coal |
| CN102430310B (en) * | 2011-10-23 | 2014-04-02 | 中冶焦耐(大连)工程技术有限公司 | A method for recovering fine particle coal |
| CN105148670A (en) * | 2015-09-17 | 2015-12-16 | 合肥中亚环保科技有限公司 | Bag-wet combined electrical dust remover |
| CN112156600A (en) * | 2020-09-19 | 2021-01-01 | 昆明理工大学 | Method and device for preventing pipeline for conveying yellow phosphorus furnace gas from being blocked and removing dust |
| CN112170010A (en) * | 2020-10-15 | 2021-01-05 | 艾尼科环保技术(安徽)有限公司 | Novel electrostatic precipitator import loudspeaker |
| CN118417057A (en) * | 2024-07-02 | 2024-08-02 | 山西省安装集团股份有限公司 | Dust removing device for heat source plant |
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Legal Events
| Date | Code | Title | Description |
|---|---|---|---|
| C14 | Grant of patent or utility model | ||
| GR01 | Patent grant | ||
| C17 | Cessation of patent right | ||
| CF01 | Termination of patent right due to non-payment of annual fee |
Granted publication date: 20060621 Termination date: 20100512 |