CN201662077U - Wet-dry process combined dust collection device - Google Patents
Wet-dry process combined dust collection device Download PDFInfo
- Publication number
- CN201662077U CN201662077U CN2010201704822U CN201020170482U CN201662077U CN 201662077 U CN201662077 U CN 201662077U CN 2010201704822 U CN2010201704822 U CN 2010201704822U CN 201020170482 U CN201020170482 U CN 201020170482U CN 201662077 U CN201662077 U CN 201662077U
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- dust
- flue
- wet
- flue dust
- wet scrubber
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Abstract
The utility model discloses a wet-dry process combined dust collection device, which comprises a wet dust collector and a cloth dust collector. The wet dust collector is connected with the flue of a kiln, the flue dust outlet of the wet dust collector is connected with a flue dust mixing compartment capable of regulating temperature and humidity of flue dust through a pipeline, and the flue dust mixing compartment is connected with the cloth dust collector. The wet-dry process combined dust collection device effectively overcomes the difficulty of burnt cloth bag or moisture condensation. The flue gas subjected to dust collection by the device exceeds the national second-class emission standard; and annular sulfur dioxide emission is not higher than 4.3 t/a, the flue dust emission is not higher than 1.06 t/a, and the fine dust emission is not higher than 0.24 t/a. The wet-dry process combined dust collection device has the advantages of low energy consumption, environmental friendliness, controllable reaction process, etc.; and the waste residue can be directly used as building raw material.
Description
Technical field
The utility model relates to a kind of dust arrester, refers in particular to a kind of dedusting that is used for the stove equipment of fire coal such as refractory material calcining furnace, high temperature, loop cycle operation and uses.
Background technology
The stove of firing refractory material is a kind of high-temperature service, is in stove various used for refractory material coals to be heated to 1390 ℃～1650 ℃ of firing temperatures, all produces pollutants such as a large amount of flue dust, sulfur dioxide, tar, carbon dust in its whole sintering procedure.The loading of kiln at normal temperatures of various refractory materials progressively is warmed up to firing temperature then, and after the insulation regular hour, drops to normal temperature naturally.The temperature of the flue dust in the flue of stove is the highest also 1350 ℃, and the flue dust temperature at the initial stage of intensification is lower, also contains a large amount of moisture.
Present dust-removal and desulfurizing equipment generally has two kinds: a kind of is wet scrubber, it is that the flue dust of will discharge from the flue of stove is incorporated into the dust-remover tower, generally speaking, flue dust enters from the bottom of tower from the top of tower and discharges, and is provided with water in the tower or other can dissolve SO
2And and SO
2The akaline liquid of reaction, when flue dust contacted with water or akaline liquid, the graininess flue dust obtained moistening, and SO
2Then water-soluble or akaline liquid.But this method does not have any effect for the polluter in the flue dust of water insoluble or alkaline solution.Another kind is a sack cleaner, and it is that flue dust is fed in the cloth bag, by the intensive filtration of cloth bag, particulate contaminants in the flue dust is stayed in the cloth bag, pollutes thereby reduce.But this dust collection method is to not effect of gas pollutant.And the burning-point of general cloth bag if the flue dust temperature is too high, then may cause the burning of cloth bag about 135 ℃, and has also collected combustible such as carbon dust in the cloth bag, can lead to a disaster.Contain moisture if enter the flue dust of cloth bag, form dewfall, can make then that flue dust is sticking to get lodged in cloth bag inside, the cloth bag space is stopped up, can not exhaust, and blown quick-fried.The temperature that resembles the flue dust that the such equipment of refractory material baking furnace discharges is very high, and also contains a large amount of moisture at the flue dust at the initial stage of intensification.If directly using bag-type dust is not that cloth bag is stopped up, cloth bag is completely burnouted.
The utility model content
The flue dust that the utility model technical issues that need to address provide a kind of High-temp. kiln to fire coal has good dust-removing sulphur removing function effect, can prevent that the control of dust cloth bag from stopping up, prolonging the dust-removal cloth-bag dust arrester in service life.
For solving the problems of the technologies described above, technical solution adopted in the utility model is:
A kind of dust arrester with wet dry method associated form, comprise wet scrubber and cloth dust collector, wet scrubber is connected with the flue of stove, the flue dust outlet of wet scrubber is connected with the flue dust allotment chamber that can regulate the flue dust temperature humidity by pipeline, and flue dust allotment chamber is connected with cloth dust collector.
Further improvement of the utility model is: the indoor drying device that is provided with of described flue dust allotment, drying device comprises the electrical drying device and/or utilizes the drier of stove waste heat heat exchange.
Further improvement of the utility model is: the indoor humidity temperature pickup that is equipped with of described flue dust allotment, humidity temperature pickup links to each other with control system, and control system also links to each other with the control device of the control device of the drier of waste heat heat exchange, electrical drying device, wet scrubber.
Further concrete structure of the present utility model is: the control device of the drier of described waste heat heat exchange comprises valve and blower fan.The drier of waste heat heat exchange adopts common corrosion-resistant, resistant to elevated temperatures material to make.
Further improvement of the utility model is: the described drier of stove waste heat heat exchange that utilizes is communicated with the flue and the wet scrubber of industrial furnace by dry flue; The valve and the blower fan of control waste heat heat exchange drier are installed on the dry flue.
Further improvement of the utility model is: also be provided with blower fan on the pipeline between described wet scrubber and the flue dust allotment chamber.
Further improvement of the utility model is: be provided with valve between described flue dust allotment chamber and the cloth dust collector.
Further improvement of the utility model is: described wet scrubber is the wherein a kind of of fountain wet scrubber or liquid film rotating vane type deduster or both combinations.
Further improvement of the utility model is: described wet scrubber below is provided with primary sedimentation basin and secondary sedimentation tank.
Owing to adopted technique scheme, the obtained technological progress of the utility model is:
The utility model has good dust-removing sulphur removing function effect, can prevent that the control of dust cloth bag from stopping up, prolonging control of dust cloth bag service life the flue dust of the High-temp. kiln of fire coal.Whole system is closed cycle, non-wastewater discharge, so water consumption is few.Be lower than national secondary discharge standard through the flue gas after this device dedusting, reach sulfur dioxide≤228mg/m
3, flue dust≤56.3mg/m
3
Sulfur dioxide and part flue dust are eliminated in bulky grain, the dissolving of wet scrubber in can moistening flue dust, simultaneously high-temperature smoke are cooled off.SO in the flue gas
2With the Ca in the alkaline solution (OH)
2React, generate CaSO
4, CaSO
3Be deposited in the sedimentation basin Deng product, can be used for the making of construction material through recovery.Spray water reusable edible after secondary precipitation makes the utility model not have discharging, and non-secondary pollution has good environmental benefit and economic benefit.Flue dust allotment chamber is regulated temperature, humidity even the precipitation of flue gas and is collected a part of particle flue dust.The waste material (main component is a carbonaceous material) that cloth dust collector is collected can be used as the common people's fuel or is used for that other is industrial, and refuse reclamation has reduced secondary pollution, has reduced operating cost.
Flue dust temperature in the stove flue is at the furnace heating-up initial stage, and the flue dust temperature is lower, also contains a large amount of moisture, and especially at northern area, winter temperature is very low, and dewfall very easily takes place.If with the regulation and control of the flue gas in the flue without flue dust allotment chamber, the cloth bag of bag collector very easily blocks.The utility model utilizes that electric heater heats, drying, the flue dust heating when kiln is initially heated up, is dried to certain temperature, humidity.Guarantee that the flue gas that enters bag collector does not block cloth bag.
The indoor humidity temperature pickup that is equipped with of flue dust allotment, too high as if the temperature that the flue dust allotment is indoor, control device can send instruction, makes wet scrubber strengthen the heat exchange dynamics, flue-gas temperature is reduced to the scope of requirement.Electrical drying device and/or utilize the drier work of stove waste heat heat exchange simultaneously, with flue gas drying within the scope of technological requirement.If smoke moisture is too high, control system is sent instruction, make the electrical drying device and/or utilize the drier work of stove waste heat heat exchange, with flue gas drying within the scope of technological requirement.Guarantee that the flue gas that enters bag collector can not block cloth bag because of humidity is excessive, can be because of temperature high scaling loss cloth bag yet.
The drier of waste heat heat exchange adopts common corrosion-resistant, resistant to elevated temperatures material to make, and utilizes the waste heat of flue gas to heat to flue gas, has reduced energy consumption, has reduced cost, meets the energy-conserving and environment-protective policy that country advocates.Wet scrubber adopts spray liquid membrane type dust-removal and desulfurizing, and the desulfuration efficiency height has been eliminated the corrosion of flue gas to blower fan.
Description of drawings
Fig. 1 is a structural principle schematic diagram of the present utility model;
Fig. 2 is the principle schematic of another kind of structure of the present utility model.
Wherein: 1, stove, 2, flue, 3, wet scrubber, 4, dry flue, 5, pipeline, 6, blower fan, 7, dry flue, 8, blower fan, 9, flue dust allotment chamber, 10, the electrical drying device, 11, pipeline, 12, valve, 13, drier, 14, humidity temperature pickup, 15, pipeline, 16, cloth dust collector, 17, chimney, 18, pipeline, 19, primary sedimentation basin, 20, pipeline, 21, secondary sedimentation tank, 22, pipeline, 23, motor, 24, valve.
The specific embodiment
Below in conjunction with the drawings and the specific embodiments the utility model is described in further details:
Embodiment 1
Present embodiment as shown in Figure 1, the flue dust of the wet scrubber 3 of dust arrester inlet is positioned at wet scrubber 3 lower ends, the flue dust inlet is connected with the stove 1 of firing refractory material by flue 2.Wet scrubber 3 is the wet scrubber that liquid membrane type and fountain combine.The upper end of wet scrubber 3 is provided with the flue dust outlet, and the flue dust outlet is connected with pipeline 5, and the other end of pipeline 5 connects flue dust allotment chamber 9, and pipeline 5 is provided with blower fan 8.The flue dust that stove 1 is discharged enters wet scrubber 3 through flue 2, and part cigarette ash dirt is eliminated in bulky grain, the dissolving of wet scrubber 3 in can moistening flue dust, and high-temperature smoke is cooled off.SO in the while flue gas
2With the alkaline solution Ca (OH) in the wet scrubber 3
2React, generate CaSO
4, CaSO
3Deng.The upper end of wet scrubber 3 is provided with the spray water inlet, inlet is connected with pipeline 22, the lower end is provided with the floss hole of collecting liquid and solid waste, floss hole is connected with pipeline 18, pipeline 18 other ends feed primary sedimentation basin 19, primary sedimentation basin 19 is connected with secondary sedimentation tank 21 by pipeline 20, and the shower water inlet of secondary sedimentation tank 21 and wet scrubber 3 upper ends is connected by pipeline 22, and pipeline 22 is provided with motor 23 and water pump.Liquid such as the flue dust of dissolving in the wet scrubber 3, degraded and solid waste successively enter primary sedimentation basin, secondary sedimentation tank.Water after secondary precipitation is recycled by pipeline 22, the CaSO of deposition in the primary sedimentation basin 19
4, CaSO
3Can be used for the making of construction material etc. Deng material, be further used in the industrial or agricultural.Whole system is closed cycle, non-wastewater discharge, so water consumption is few, non-secondary pollution has good environmental benefit and economic benefit.The waste material that wet scrubber 3 is collected can be used as construction material etc. and recycles in other industrially after secondary precipitation, and the utilization again of refuse has reduced secondary pollution, has reduced operating cost.
Flue dust is through behind the desulfurization and dedusting of wet scrubber 3, under the effect of blower fan 8, enter flue dust allotment chamber 9 through pipeline 5, flue dust allotment chamber 9 is provided with flue dust inlet, flue dust outlet, inside is provided with drier 13, electrical drying device 10 and the humidity temperature pickup 14 of waste heat heat exchange, the flue dust inlet of flue dust allotment chamber 9 is connected with pipeline 5, the flue dust outlet links to each other with cloth dust collector 16 by pipeline 11, and pipeline 11 is provided with valve 24.Drier 13 1 ends of waste heat heat exchange are connected with flue 2 by dry flue 4, and dry flue 4 is provided with valve 12, and the other end is connected with wet scrubber 3 by dry flue 7, and dry flue 7 is provided with blower fan 6.If enter the temperature of the flue dust of flue dust allotment chamber 9 when reaching the higher limit of setting, humidity temperature pickup 14 can pass to control system with detection signal, control system can make the motor 23 of wet scrubber start working, strengthen spray flux, strengthen wet scrubber 3 heat exchange dynamics, the flue dust temperature is reduced to the scope of requirement.When excessive as if the humidity of the flue dust that enters flue dust allotment chamber 9, humidity temperature pickup 14 can pass to control system with detection signal, control system can make electrical drying device 10 and/or drier 13 start working, and flue dust is dehumidified, and it is met the requirements of within the scope.If it is too high or humidity is excessive to enter the temperature of flue dust of flue dust allotment chamber 9, control system will make valve 24 close, and avoid causing danger; After being formulated to flue dust in the claimed range, control system is sent instruction, opens valve 24, and flue dust enters cloth dust collector 16 through pipeline 11.Through the allotment of flue dust allotment chamber 9, guarantee that the flue gas that enters cloth dust collector 16 can not block cloth bag because of humidity is excessive, can be because of temperature high scaling loss cloth bag yet.
Embodiment 2
Present embodiment as shown in Figure 2, be with the difference of embodiment 1: the indoor humidity of 10 pairs of flue dust of electrical drying device of only using of the allotment of present embodiment is regulated, the temperature of flue dust is controlled by the amount of liquid that wet scrubber 3 feeds, and makes the temperature and humidity of the flue dust that enters sack cleaner all meet the requirements of scope.
Claims (9)
1. dust arrester with wet dry method associated form, comprise wet scrubber (3) and cloth dust collector (16), it is characterized in that: wet scrubber (3) is connected with the flue (2) of stove, the flue dust outlet of wet scrubber (3) is connected with the flue dust allotment chamber (9) that can regulate the flue dust temperature humidity by pipeline (5), and flue dust allotment chamber (9) is connected with cloth dust collector (16).
2. a kind of dust arrester according to claim 1 with wet dry method associated form, it is characterized in that: be provided with drying device in the described flue dust allotment chamber (9), drying device comprises electrical drying device (10) and/or utilizes the drier (13) of stove waste heat heat exchange.
3. a kind of dust arrester according to claim 2 with wet dry method associated form, it is characterized in that: in the described flue dust allotment chamber (9) humidity temperature pickup (14) is installed, humidity temperature pickup (14) links to each other with control system, and control system also links to each other with the control device of the control device of the drier (13) of waste heat heat exchange, electrical drying device (10), wet scrubber (3).
4. a kind of dust arrester with wet dry method associated form according to claim 3 is characterized in that: the control device of the drier of described waste heat heat exchange (13) comprises valve (12) and blower fan (6).
5. according to each described a kind of dust arrester with wet dry method associated form of claim 2～4, it is characterized in that: the described drier (13) of stove waste heat heat exchange that utilizes is communicated with the flue (2) and the wet scrubber (3) of industrial furnace by dry flue (4); The valve (12) and the blower fan (6) of control waste heat heat exchange drier (13) are installed on the dry flue (4,7).
6. according to each described a kind of dust arrester of claim 1～4, it is characterized in that: also be provided with blower fan (8) on the pipeline (5) between described wet scrubber (3) and the flue dust allotment chamber (9) with wet dry method associated form.
7. according to each described a kind of dust arrester of claim 1～4, it is characterized in that: be provided with valve (24) between described flue dust allotment chamber (9) and the cloth dust collector (16) with wet dry method associated form.
8. a kind of dust arrester with wet dry method associated form according to claim 1 is characterized in that: described wet scrubber (3) is the wherein a kind of of fountain wet scrubber or liquid film rotating vane type deduster or both combinations.
9. according to claim 1 or 8 described a kind of dust arresters with wet dry method associated form, it is characterized in that: described wet scrubber (3) below is provided with primary sedimentation basin (19) and secondary sedimentation tank (21).
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN2010201704822U CN201662077U (en) | 2010-04-27 | 2010-04-27 | Wet-dry process combined dust collection device |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN2010201704822U CN201662077U (en) | 2010-04-27 | 2010-04-27 | Wet-dry process combined dust collection device |
Publications (1)
| Publication Number | Publication Date |
|---|---|
| CN201662077U true CN201662077U (en) | 2010-12-01 |
Family
ID=43232494
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| CN2010201704822U Expired - Lifetime CN201662077U (en) | 2010-04-27 | 2010-04-27 | Wet-dry process combined dust collection device |
Country Status (1)
| Country | Link |
|---|---|
| CN (1) | CN201662077U (en) |
Cited By (4)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN102235679A (en) * | 2010-04-27 | 2011-11-09 | 封彦彦 | Dust removing device with wet and dry method combined mode |
| CN103657281A (en) * | 2013-11-26 | 2014-03-26 | 潘高峰 | Dust removing system |
| CN105477943A (en) * | 2016-01-14 | 2016-04-13 | 成都瑞柯林工程技术有限公司 | Method for controlling moisture on air filtering elements |
| CN105805769A (en) * | 2016-03-24 | 2016-07-27 | 江苏联兴成套设备制造有限公司 | Operation process of pyrolysis gasifier heat-transfer oil fume heating device |
-
2010
- 2010-04-27 CN CN2010201704822U patent/CN201662077U/en not_active Expired - Lifetime
Cited By (4)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN102235679A (en) * | 2010-04-27 | 2011-11-09 | 封彦彦 | Dust removing device with wet and dry method combined mode |
| CN103657281A (en) * | 2013-11-26 | 2014-03-26 | 潘高峰 | Dust removing system |
| CN105477943A (en) * | 2016-01-14 | 2016-04-13 | 成都瑞柯林工程技术有限公司 | Method for controlling moisture on air filtering elements |
| CN105805769A (en) * | 2016-03-24 | 2016-07-27 | 江苏联兴成套设备制造有限公司 | Operation process of pyrolysis gasifier heat-transfer oil fume heating device |
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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: 20101201 Effective date of abandoning: 20130417 |
|
| RGAV | Abandon patent right to avoid regrant |