CN203253300U - Bubble type spray desulphurization dust collector - Google Patents
Bubble type spray desulphurization dust collector Download PDFInfo
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- CN203253300U CN203253300U CN 201320154651 CN201320154651U CN203253300U CN 203253300 U CN203253300 U CN 203253300U CN 201320154651 CN201320154651 CN 201320154651 CN 201320154651 U CN201320154651 U CN 201320154651U CN 203253300 U CN203253300 U CN 203253300U
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- China
- Prior art keywords
- reaction zone
- bubbling
- area
- smoke chamber
- entrance smoke
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- 239000007921 spray Substances 0.000 title claims abstract description 14
- 239000000428 dust Substances 0.000 title abstract description 22
- 238000006243 chemical reaction Methods 0.000 claims abstract description 23
- 230000005587 bubbling Effects 0.000 claims abstract description 21
- 235000019738 Limestone Nutrition 0.000 claims abstract description 12
- 239000006028 limestone Substances 0.000 claims abstract description 12
- 239000007788 liquid Substances 0.000 claims abstract description 10
- 238000006477 desulfuration reaction Methods 0.000 claims abstract description 7
- 230000023556 desulfurization Effects 0.000 claims abstract description 7
- 125000006850 spacer group Chemical group 0.000 claims 2
- 230000015572 biosynthetic process Effects 0.000 claims 1
- 238000005859 coupling reaction Methods 0.000 claims 1
- 239000012716 precipitator Substances 0.000 claims 1
- 238000005192 partition Methods 0.000 abstract description 19
- 239000000779 smoke Substances 0.000 abstract description 13
- 238000000746 purification Methods 0.000 abstract description 10
- 239000002002 slurry Substances 0.000 abstract description 10
- UGFAIRIUMAVXCW-UHFFFAOYSA-N Carbon monoxide Chemical compound [O+]#[C-] UGFAIRIUMAVXCW-UHFFFAOYSA-N 0.000 abstract description 8
- 239000003546 flue gas Substances 0.000 abstract description 8
- 229910052799 carbon Inorganic materials 0.000 abstract description 3
- 230000000694 effects Effects 0.000 abstract description 3
- 238000004519 manufacturing process Methods 0.000 abstract description 3
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 abstract description 2
- 230000007613 environmental effect Effects 0.000 abstract description 2
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 9
- 239000007789 gas Substances 0.000 description 8
- 239000002245 particle Substances 0.000 description 8
- 230000002745 absorbent Effects 0.000 description 2
- 239000002250 absorbent Substances 0.000 description 2
- 239000000376 reactant Substances 0.000 description 2
- NINIDFKCEFEMDL-UHFFFAOYSA-N Sulfur Chemical compound [S] NINIDFKCEFEMDL-UHFFFAOYSA-N 0.000 description 1
- 230000015271 coagulation Effects 0.000 description 1
- 238000005345 coagulation Methods 0.000 description 1
- 239000003245 coal Substances 0.000 description 1
- 238000005260 corrosion Methods 0.000 description 1
- 238000005265 energy consumption Methods 0.000 description 1
- 239000010438 granite Substances 0.000 description 1
- 238000000034 method Methods 0.000 description 1
- 229910052717 sulfur Inorganic materials 0.000 description 1
- 239000011593 sulfur Substances 0.000 description 1
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- Treating Waste Gases (AREA)
Abstract
一种鼓泡式喷淋脱硫除尘器,入口烟室连接反应区形成进气通道,入口烟室的底端连有喷淋管,所述反应区的上端依次上下错开连接上隔板和下隔板形成鼓泡区,所述反应区的下端设有石灰石浆池,鼓泡区中的下隔板直接插入沉灰池的液面以下,所述反应区的侧壁设有出气口。本实用新型的技术效果是:提高燃煤烟气的净化效率,有效地达到脱硫除尘的目的,外型简单,制作成本低,节约能源,环保,低碳。
A bubbling spray desulfurization deduster, the entrance smoke chamber is connected with the reaction zone to form an air intake channel, the bottom end of the entrance smoke chamber is connected with a spray pipe, and the upper end of the reaction zone is sequentially staggered up and down to connect the upper partition and the lower partition The plates form a bubbling area, the lower end of the reaction area is provided with a limestone slurry tank, the lower partition in the bubbling area is directly inserted below the liquid level of the ash settling tank, and the side wall of the reaction area is provided with an air outlet. The technical effects of the utility model are: improving the purification efficiency of coal-fired flue gas, effectively achieving the purpose of desulfurization and dust removal, simple appearance, low production cost, energy saving, environmental protection, and low carbon.
Description
本实用新型涉除尘器,尤其涉及一种鼓泡式喷淋脱硫除尘器。 The utility model relates to a dust remover, in particular to a bubbling spray desulfurization dust remover.
背景技术 Background technique
常见的湿法脱硫除尘净化设备有喷雾式、旋风式、储水冲击水浴式、塔板式、文丘里等。但通常由于烟气中含硫,与水接触后使得除尘设备容易腐蚀。其次由于受各种因素的限制,单个除尘器的除尘效率不是很高。 Common wet desulfurization and dust removal purification equipment include spray type, cyclone type, water storage impact water bath type, tray type, Venturi type, etc. However, usually due to the sulfur in the flue gas, the dust removal equipment is easy to corrode after contacting with water. Secondly, due to the limitation of various factors, the dust removal efficiency of a single dust collector is not very high.
发明内容 Contents of the invention
本实用新型的目的在于提供了一种鼓泡式喷淋脱硫除尘器,该装置采用花岗岩材质,有防腐蚀的作用,由于结合了喷淋式,和鼓泡式,这就有效地提高了含硫燃煤烟气的净化除尘效率,设备外型结构简单,降低了设备制作成本,降低使用过程中的能耗,低碳环保。 The purpose of this utility model is to provide a bubbling spray desulfurization and dedusting device, which is made of granite and has the effect of anti-corrosion. The purification and dust removal efficiency of sulfur-fired coal flue gas, the appearance and structure of the equipment are simple, which reduces the cost of equipment manufacturing, reduces energy consumption during use, and is low-carbon and environmentally friendly.
本实用新型是这样来实现的,它包括入口烟室、反应区、喷淋管、上隔板、下隔板、石灰石浆池、出气口,入口烟室连接反应区形成进气通道,其特征是入口烟室的底端连有喷淋管,所述反应区的上端依次上下错开连接上隔板和下隔板形成鼓泡区,所述反应区的下端设有石灰石浆池,鼓泡区中的下隔板直接插入沉灰池的液面以下,所述反应区的侧壁设有出气口。 The utility model is achieved in this way, it includes the entrance smoke chamber, reaction area, spray pipe, upper partition, lower partition, limestone slurry pool, air outlet, the entrance smoke chamber is connected with the reaction area to form an air inlet channel, its characteristic The bottom of the entrance smoke chamber is connected with a spray pipe, and the upper end of the reaction zone is staggered up and down to connect the upper partition and the lower partition to form a bubbling zone. The lower end of the reaction zone is provided with a limestone slurry pool, and the bubbling zone The lower partition in the middle is directly inserted below the liquid level of the ash settling tank, and the side wall of the reaction zone is provided with an air outlet.
烟气进入入口烟室,在入口烟室的底端接喷淋管,气体进入除尘器后立即喷淋,粉尘被雾化的液滴润湿,尘粒与水滴或尘粒与尘粒发生凝聚更易于被捕集,充分接触后达到第一次净化。随后的结构是由上下隔板组成的鼓泡区,鼓泡区的下端布置了石灰石浆池,鼓泡区中的下隔板直接插入沉灰池的液面以下,使得从入口烟室过来的气体再次连续冲击水面,达到第二次净化。鼓泡区气泡不断大量而迅速地生成和破裂使气液接触进一步加强,不断产生新的接触面,同时将反应物由鼓泡区传递至反应区,反应区存在大量的气泡,并使新鲜的吸收剂与烟气接触。气流中的粉尘粒子被石灰石浆池的水膜捕获,净化后的气体由出气口排出,达到高效率的净化。 The flue gas enters the entrance smoke chamber, and the bottom of the entrance smoke chamber is connected with a spray pipe. After the gas enters the dust collector, it is sprayed immediately, and the dust is wetted by the atomized liquid droplets, and the dust particles and water droplets or dust particles and dust particles condense It is easier to be trapped and achieve the first purification after full contact. The subsequent structure is a bubbling area composed of upper and lower partitions. A limestone slurry pool is arranged at the lower end of the bubbling area. The lower partition in the bubbling area is directly inserted below the liquid level of the ash settling tank, so that The gas hits the water surface continuously again to achieve the second purification. Bubbles in the bubbling area are continuously and rapidly generated and broken to further strengthen the gas-liquid contact, and new contact surfaces are constantly generated, and at the same time, the reactants are transferred from the bubbling area to the reaction area. There are a large number of air bubbles in the reaction area, and the fresh The absorbent comes into contact with the flue gas. The dust particles in the airflow are captured by the water film of the limestone slurry tank, and the purified gas is discharged from the gas outlet to achieve high-efficiency purification.
本实用新型的技术效果是:提高燃煤烟气的净化效率,有效地达到脱硫除尘的目的,外型简单,制作成本低,节约能源,环保,低碳。 The technical effects of the utility model are: improving the purification efficiency of coal-fired flue gas, effectively achieving the purpose of desulfurization and dust removal, simple appearance, low production cost, energy saving, environmental protection, and low carbon.
附图说明 Description of drawings
图1为本实用新型的结构示意图。 Fig. 1 is the structural representation of the utility model.
在图中,1、入口烟室 2、反应区 3、喷淋管 4、上隔板 5、下隔板 6、石灰石浆池 7、出气口。 In the figure, 1. Entrance smoke chamber 2. Reaction area 3. Spray pipe 4. Upper partition 5. Lower partition 6. Limestone slurry pool 7. Air outlet.
具体实施方式 Detailed ways
如图1所示,本实用新型是这样来实现的,它包括入口烟室1、反应区2、喷淋管3、上隔板4、下隔板5、石灰石浆池6、出气口7,入口烟室1连接反应区2形成进气通道,入口烟室1的底端连有喷淋管3,所述反应区2的上端依次上下错开连接上隔板4和下隔板5形成鼓泡区,所述反应区2的下端设有石灰石浆池6,鼓泡区中的下隔板5直接插入沉灰池6的液面以下,所述反应区2的侧壁设有出气口7。当烟气进入入口烟室,在入口烟室的底端接喷淋管,气体进入除尘器后立即喷淋,粉尘被雾化的液滴润湿,尘粒与水滴或尘粒与尘粒发生凝聚更易于被捕集,充分接触后达到第一次净化。随后的结构是由上下隔板组成的鼓泡区,鼓泡区的下端布置了石灰石浆池,鼓泡区中的下隔板直接插入沉灰池的液面以下,使得从入口烟室过来的气体再次连续冲击水面,达到第二次净化。鼓泡区气泡不断大量而迅速地生成和破裂使气液接触进一步加强,不断产生新的接触面,同时将反应物由鼓泡区传递至反应区,反应区存在大量的气泡,并使新鲜的吸收剂与烟气接触。气流中的粉尘粒子被石灰石浆池的水膜捕获,净化后的气体由出气口排出,达到高效率的净化。 As shown in Figure 1, the utility model is realized in this way, which includes an inlet smoke chamber 1, a reaction zone 2, a spray pipe 3, an upper partition 4, a lower partition 5, a limestone slurry pool 6, and an air outlet 7. The entrance smoke chamber 1 is connected to the reaction zone 2 to form an air intake channel, and the bottom end of the entrance smoke chamber 1 is connected with a spray pipe 3, and the upper end of the reaction zone 2 is sequentially staggered up and down to connect the upper partition 4 and the lower partition 5 to form bubbling The lower end of the reaction zone 2 is provided with a limestone slurry tank 6, the lower partition 5 in the bubbling zone is directly inserted below the liquid level of the ash settling tank 6, and the side wall of the reaction zone 2 is provided with an air outlet 7. When the flue gas enters the entrance smoke chamber, the bottom of the entrance smoke chamber is connected with a spray pipe, and the gas is sprayed immediately after entering the dust collector, and the dust is wetted by the atomized liquid droplets, and dust particles and water droplets or dust particles and dust particles Coagulation is easier to be trapped, and the first purification is achieved after sufficient contact. The subsequent structure is a bubbling area composed of upper and lower partitions. A limestone slurry pool is arranged at the lower end of the bubbling area. The lower partition in the bubbling area is directly inserted below the liquid level of the ash settling tank, so that The gas hits the water surface continuously again to achieve the second purification. Bubbles in the bubbling area are continuously and rapidly generated and broken to further strengthen the gas-liquid contact, and new contact surfaces are constantly generated, and at the same time, the reactants are transferred from the bubbling area to the reaction area. There are a large number of air bubbles in the reaction area, and the fresh The absorbent comes into contact with the flue gas. The dust particles in the airflow are captured by the water film of the limestone slurry tank, and the purified gas is discharged from the gas outlet to achieve high-efficiency purification.
Claims (1)
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN 201320154651 CN203253300U (en) | 2013-04-01 | 2013-04-01 | Bubble type spray desulphurization dust collector |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN 201320154651 CN203253300U (en) | 2013-04-01 | 2013-04-01 | Bubble type spray desulphurization dust collector |
Publications (1)
| Publication Number | Publication Date |
|---|---|
| CN203253300U true CN203253300U (en) | 2013-10-30 |
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| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| CN 201320154651 Expired - Fee Related CN203253300U (en) | 2013-04-01 | 2013-04-01 | Bubble type spray desulphurization dust collector |
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| Country | Link |
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| CN (1) | CN203253300U (en) |
Cited By (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN104474870A (en) * | 2014-12-08 | 2015-04-01 | 冯学岭 | Novel desulfurization dust remover |
| CN119258696A (en) * | 2024-09-02 | 2025-01-07 | 江苏国鹰环境科技有限公司 | A composite paint mist filter |
-
2013
- 2013-04-01 CN CN 201320154651 patent/CN203253300U/en not_active Expired - Fee Related
Cited By (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN104474870A (en) * | 2014-12-08 | 2015-04-01 | 冯学岭 | Novel desulfurization dust remover |
| CN119258696A (en) * | 2024-09-02 | 2025-01-07 | 江苏国鹰环境科技有限公司 | A composite paint mist filter |
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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: 20131030 Termination date: 20140401 |
