CN204933245U - Industrial smoke embrane method gathers dirt devulcanizer - Google Patents
Industrial smoke embrane method gathers dirt devulcanizer Download PDFInfo
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- CN204933245U CN204933245U CN201520707027.4U CN201520707027U CN204933245U CN 204933245 U CN204933245 U CN 204933245U CN 201520707027 U CN201520707027 U CN 201520707027U CN 204933245 U CN204933245 U CN 204933245U
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- housing
- embrane method
- industrial smoke
- film bubble
- exhaust outlet
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Abstract
Industrial smoke embrane method gathers dirt devulcanizer, comprises housing, and housing is provided with air inlet and exhaust outlet; Be provided with flow straightener in housing, flow straightener is positioned at the dead ahead of air inlet; On housing and/or flow straightener be provided with elecrtonegativity film bubble charity device, lower housing portion is dust hopper.The utility model effectively can solve collection and the trapping problem of the extremely strong micronic dust of penetration power (aerosol PM2.5), effectively can remove micronic dust in industrial enterprise's flue gas (aerosol PM10 and PM2.5) and SO
2, thus effectively complete poly-dirt and desulfurization.
Description
Technical field
The utility model relates to equipment manufacture of environmental protection field, is specifically related to a kind of industrial smoke embrane method and gathers dirt devulcanizer.
Background technology
As everyone knows, industrial waste gas or construction field waste gas are one of primary pollution source of ambient air, and that causes ambient air dust haze to pollute mainly contains micronic dust (PM2.5 aerosol) and SO
2, NO
xdeng, ambient air pollutes and causes huge harm to the health of the mankind.
For solving waste gas to the severe contamination problem of ambient air, various countries scientific worker has carried out effort in a sustained way.But existing cleaner system and measure, as the sack cleaner of current techniques advanced person, electric cleaner, electric bag joint dedusting device and huge water washing dedust facility and huge foam dust-removing Tower System, collection or the trapping problem of the extremely strong micronic dust of penetration power (PM2.5 aerosol) all effectively can not be solved.The filter material of to be aperture the be molecule level effectively filtering micronic dust (PM2.5 aerosol) in existing technical equipment system, only can solve the limited quantity gas cleaning in the confined space, and corresponding system apparatus cost is high, processing cost is high, for tens thousand of extremely millions of cubic meter/industry hourly or engineering waste gas are had no idea completely easily.
Objectively, the current effective way alleviating or reduce ambient air pollution level only has strange land to move, or the implementing limited production to industrial enterprise or interim to stop production of policy.
In industrial furnace smoke desulfurization, current application effectively invests ten million to several hundred million ten thousand yuan a set of desulfurizer systems easily, desulfuration efficiency is in fact on the low side, and desulphurization cost is higher, the situation of regular appearance is, invest tens million of unit and build desulfurizer, only just enable under the severe inspection of supervision.Huge with operating cost problem because investing for the medium-sized and small enterprises had a large capacity and a wide range, more owing to not investing little effective desulfurizer system, the solution that Bian gets tries every possible means to escape the Environment Protection Responsibility of flue gas desulfurization.
For this reason, in the urgent need to a kind of can effectively to industrial fumes waste gas dedusting haze and the purifying device compared with Low investment, low operating cost of SO2.
Utility model content
Technical problem to be solved in the utility model is, overcome the deficiency of above-mentioned background technology, a kind of industrial smoke embrane method is provided to gather dirt devulcanizer, this poly-dirt devulcanizer effectively can solve collection and the trapping problem of the extremely strong micronic dust of penetration power (aerosol PM2.5), effectively can remove micronic dust in industrial enterprise's flue gas (aerosol PM10 and PM2.5) and SO
2, effectively complete poly-dirt and desulfurization.
The technical scheme that the utility model solves the employing of its technical problem is that a kind of industrial smoke embrane method gathers dirt devulcanizer, comprises housing, and described housing is provided with air inlet and exhaust outlet; Be provided with flow straightener in described housing, described flow straightener is positioned at the dead ahead of air inlet; On described housing and/or flow straightener be provided with elecrtonegativity film bubble charity device, described lower housing portion is dust hopper.
Further, described housing middle and lower part is provided with access door.
Further, in described housing, nearly exhaust port side is also fixed with filtration members.
Further, described filtration members comprises framework, and described framework is fixed on nearly exhaust port side in housing, described framework is fixed with filter screen and dust remover.
Further, described dust hopper bottom is connected with deslagging conveyer.
Further, described exhaust port side is provided with exhaust fan, and described exhaust outlet is connected with the air inlet duct of exhaust fan.
Further, described housing is vertically arranged, described air inlet is positioned at the side of housing, and described exhaust outlet is positioned at case top.
Further, described housing is horizontally disposed, and described air inlet is positioned at the side of housing, and described exhaust outlet is positioned at the opposite side of housing.
Further, described elecrtonegativity film bubble charity device is bar type elecrtonegativity film bubble charity device or ring-type elecrtonegativity film bubble charity device.
Compared with prior art, advantage of the present utility model is as follows:
(1) flue gas enters embrane method by air inlet and gathers in dirt devulcanizer, gather the flexible film bubble of the elecrtonegativity macromolecular material producing a large amount of flexibles in dirt devulcanizer in embrane method and load with desulfurizing agent, the flexible film bubble of elecrtonegativity macromolecular material is loaded with desulfurizing agent and is floated in flue gas stream, on the one hand, in flue gas stream, attract with the negative electrostatic of water-solubility membrane phase the imperceptible micro dust particle aerosol (PM2.5, PM10 electropositive micronic dust) assembling positively charged in flue gas, effectively can solve collection and the trapping problem of the extremely strong micronic dust of penetration power (aerosol PM2.5); On the other hand, attached desulfurizing agent is carried mutually with the high molecular weight water soluble polymer film bubble of stability with the good mechanical strength that has of superhigh specific surface area, greatly expand the haptoreaction area of desulfurizing agent and flue gas, simultaneously, there is flexible elecrtonegativity film bubble disturbance flue gas stream in a large number, and significantly increase the drift time of contact with flue gas, to reach the effect of high-efficiency desulfurization, micronic dust in industrial enterprise's flue gas (aerosol PM10 and PM2.5) and SO effectively can be removed
2, thus effectively complete poly-dirt and desulfurization.
(2) can equip as the purification of the dusty gas of non-industrial furnace smoke, solve the gas cleaning in larger space, wide adaptability and effective, be adapted to the purifying process of waste gas micronic dust of different scales, different environmental protection equipment status.
(3) structure is simple, and cost is low, and meanwhile, poly-dirt desulfurization is simple and efficient, and operating cost is lower, is easy to apply.
Accompanying drawing explanation
Fig. 1 is the structural representation of the utility model embodiment 1.
Fig. 2 is the structural representation of the utility model embodiment 2.
Fig. 3 is the structural representation of the utility model embodiment 3.
Fig. 4 is the structural representation of the utility model embodiment 4.
In figure: 1-housing, 2-elecrtonegativity film bubble charity device, 3-flow straightener, 4-filtration members, 5-exhaust fan, 6-dust hopper, 7-deslagging conveyer, 8-access door, 101-air inlet, 102-exhaust outlet, 201-bar type elecrtonegativity film bubble charity device, 202-ring-type elecrtonegativity film bubble charity device, 401-framework, 402-filter screen, 403-dust remover.
Detailed description of the invention
Below in conjunction with drawings and the specific embodiments, the utility model is described in further detail.
Embodiment 1
With reference to Fig. 1, the present embodiment comprises housing 1, and housing 1 is vertically arranged, housing 1 side is provided with air inlet 101, housing 1 top is provided with exhaust outlet 102, housing 1 is provided with 4 elecrtonegativity film bubble charity devices 2, and elecrtonegativity film bubble charity device 2 is secured by bolts on housing 1, and 4 elecrtonegativity film bubble charity devices 2 are uniformly distributed, flow straightener 3 is provided with in housing 1, flow straightener 3 is positioned at the dead ahead of air inlet 101, and housing 1 bottom is dust hopper 6, and housing 1 middle and lower part is provided with access door 8.
Embodiment 2
With reference to Fig. 2, the difference of the present embodiment and embodiment 1 is only: the quantity of elecrtonegativity film bubble charity device 2 is 1, and elecrtonegativity film bubble charity device 2 is secured by bolts on the flow straightener 3 in housing 1.All the other are with embodiment 1.
Embodiment 3
With reference to Fig. 3, the difference of the present embodiment and embodiment 1 is only: the quantity of elecrtonegativity film bubble charity device 2 is 6, and 6 elecrtonegativity film bubble charity devices 2 are secured by bolts on the housing 1 of air inlet 101 end; In housing 1, nearly exhaust outlet 102 end is also fixed with filtration members 4, and filtration members 4 comprises framework 401, and framework 401 is fixed on nearly exhaust outlet 102 end in housing 1, framework 401 is fixed with filter screen 402 and dust remover 403; Dust hopper 6 bottom is connected with deslagging conveyer 7.All the other are with embodiment 1.
Embodiment 4
With reference to Fig. 4, the difference of the present embodiment and embodiment 1 is only: housing 1 is horizontally disposed, and air inlet 101 is positioned at the side of housing 1, and exhaust outlet 102 is positioned at the opposite side of housing 1; The housing 1 of air inlet 101 end is connected with 4 bar type elecrtonegativity film bubble charity devices 201 by bolt, affixed 1 ring-type elecrtonegativity film bubble charity device 202 on flow straightener 3; Exhaust outlet 102 end is provided with exhaust fan 5, and exhaust outlet 102 is connected with the air inlet duct of exhaust fan 5; In housing 1, nearly exhaust outlet 102 end is also fixed with filtration members 4, filtration members 4 comprises framework 401, and framework 401 is fixed on nearly exhaust outlet 102 end in housing 1, framework 401 is fixed with filter screen 402 and dust remover 403, filter screen 402 is for stopping that film bubble is excessive, and dust remover 403 is for periodically clean filter screen 402; Dust hopper 6 bottom is connected with deslagging conveyer 7.All the other are with embodiment 1.
Flue gas enters embrane method by air inlet 101 and gathers in dirt devulcanizer, gather the flexible film bubble of the elecrtonegativity macromolecular material producing a large amount of flexibles in dirt devulcanizer in embrane method and load with desulfurizing agent, the flexible film bubble of elecrtonegativity macromolecular material is loaded with desulfurizing agent and is floated in flue gas stream, on the one hand, attract with the negative electrostatic of water-solubility membrane phase the imperceptible micro dust particle aerosol (PM2.5 assembling positively charged in flue gas in flue gas stream, PM10 electropositive micronic dust), simultaneously, with the adhesion characteristics of the water-soluble polymer films of superhigh specific surface area bubble phase, superfine micro dust particle (PM2.5 in adsorpting aggregation flue gas, PM10 micronic dust), thus will the superfine micronic dust (PM2.5 collected be difficult to, PM10 micronic dust) to be condensed into high molecular weight water soluble polymer be the thicker particle of carrier, the micronic dust pole adhered to is difficult to depolymerization dust again, be convenient to deduster collect, also easy sedimentation or enter gravitational settling in air in flue gas stream, thus the dust pollution thing effectively removed in Industrial Stoves discharge flue gas, on the other hand, attached desulfurizing agent is carried mutually with the high molecular weight water soluble polymer film bubble of stability with the good mechanical strength that has of superhigh specific surface area, greatly expand the haptoreaction area of desulfurizing agent and flue gas, simultaneously, there is flexible elecrtonegativity film bubble disturbance flue gas stream in a large number, and significantly increase the drift time of contact with flue gas, to reach the effect of high-efficiency desulfurization, micronic dust in industrial enterprise's flue gas (aerosol PM10 and PM2.5) and SO effectively can be removed
2, thus effectively complete poly-dirt and desulfurization.
Those skilled in the art can carry out various modifications and variations to the utility model embodiment; if these amendments and modification are within the scope of the utility model claim and equivalent technologies thereof, then these revise and modification also within protection domain of the present utility model.
The prior art that the content do not described in detail in description is known to the skilled person.
Claims (10)
1. industrial smoke embrane method gathers a dirt devulcanizer, it is characterized in that: comprise housing (1), and described housing (1) is provided with air inlet (101) and exhaust outlet (102); Be provided with flow straightener (3) in described housing (1), described flow straightener (3) is positioned at the dead ahead of air inlet (101); Described housing (1) is gone up and/or flow straightener (3) is provided with elecrtonegativity film bubble charity device (2), and described housing (1) bottom is dust hopper (6).
2. industrial smoke embrane method as claimed in claim 1 gathers dirt devulcanizer, it is characterized in that: described housing (1) middle and lower part is provided with access door (8).
3. industrial smoke embrane method as claimed in claim 1 or 2 gathers dirt devulcanizer, it is characterized in that: in described housing (1), nearly exhaust outlet (102) end is also fixed with filtration members (4).
4. industrial smoke embrane method as claimed in claim 3 gathers dirt devulcanizer, it is characterized in that: described filtration members (4) comprises framework (401), described framework (401) is fixed on nearly exhaust outlet (102) end in housing (1), described framework (401) is fixed with filter screen (402) and dust remover (403).
5. industrial smoke embrane method as claimed in claim 1 or 2 gathers dirt devulcanizer, it is characterized in that: described dust hopper (6) bottom is connected with deslagging conveyer (7).
6. industrial smoke embrane method as claimed in claim 1 or 2 gathers dirt devulcanizer, it is characterized in that: described exhaust outlet (102) end is provided with exhaust fan (5), and described exhaust outlet (102) is connected with the air inlet duct of exhaust fan (5).
7. industrial smoke embrane method as claimed in claim 1 or 2 gathers dirt devulcanizer, and it is characterized in that: described housing (1) is vertically arranged, described air inlet (101) is positioned at the side of housing (1), and described exhaust outlet (102) is positioned at housing (1) top.
8. industrial smoke embrane method as claimed in claim 1 or 2 gathers dirt devulcanizer, and it is characterized in that: described housing (1) is horizontally disposed, described air inlet (101) is positioned at the side of housing (1), and described exhaust outlet (102) is positioned at the opposite side of housing (1).
9. industrial smoke embrane method as claimed in claim 1 or 2 gathers dirt devulcanizer, it is characterized in that: described elecrtonegativity film bubble charity device (2) is bar type elecrtonegativity film bubble charity device (201) or ring-type elecrtonegativity film bubble charity device (202).
10. industrial smoke embrane method as claimed in claim 3 gathers dirt devulcanizer, it is characterized in that: described elecrtonegativity film bubble charity device (2) is bar type elecrtonegativity film bubble charity device (201) or ring-type elecrtonegativity film bubble charity device (202).
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN201520707027.4U CN204933245U (en) | 2015-09-14 | 2015-09-14 | Industrial smoke embrane method gathers dirt devulcanizer |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN201520707027.4U CN204933245U (en) | 2015-09-14 | 2015-09-14 | Industrial smoke embrane method gathers dirt devulcanizer |
Publications (1)
| Publication Number | Publication Date |
|---|---|
| CN204933245U true CN204933245U (en) | 2016-01-06 |
Family
ID=55000704
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| CN201520707027.4U Withdrawn - After Issue CN204933245U (en) | 2015-09-14 | 2015-09-14 | Industrial smoke embrane method gathers dirt devulcanizer |
Country Status (1)
| Country | Link |
|---|---|
| CN (1) | CN204933245U (en) |
Cited By (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN105107370A (en) * | 2015-09-14 | 2015-12-02 | 湖南省小尹无忌环境能源科技开发有限公司 | Membrane method dust collecting and desulfurizing device for industrial smoke |
-
2015
- 2015-09-14 CN CN201520707027.4U patent/CN204933245U/en not_active Withdrawn - After Issue
Cited By (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN105107370A (en) * | 2015-09-14 | 2015-12-02 | 湖南省小尹无忌环境能源科技开发有限公司 | Membrane method dust collecting and desulfurizing device for industrial smoke |
| CN105107370B (en) * | 2015-09-14 | 2017-10-27 | 湖南省小尹无忌环境能源科技开发有限公司 | A kind of poly- dirt devulcanizer of industrial smoke embrane method |
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Legal Events
| Date | Code | Title | Description |
|---|---|---|---|
| C14 | Grant of patent or utility model | ||
| GR01 | Patent grant | ||
| AV01 | Patent right actively abandoned |
Granted publication date: 20160106 Effective date of abandoning: 20171027 |
|
| AV01 | Patent right actively abandoned |