[go: up one dir, main page]

CN201073590Y - Absorbing tower with flue gas desulfurization - Google Patents

Absorbing tower with flue gas desulfurization Download PDF

Info

Publication number
CN201073590Y
CN201073590Y CNU200720091084XU CN200720091084U CN201073590Y CN 201073590 Y CN201073590 Y CN 201073590Y CN U200720091084X U CNU200720091084X U CN U200720091084XU CN 200720091084 U CN200720091084 U CN 200720091084U CN 201073590 Y CN201073590 Y CN 201073590Y
Authority
CN
China
Prior art keywords
demister
flue gas
inlet
tower
slurry
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
Application number
CNU200720091084XU
Other languages
Chinese (zh)
Inventor
焦安亮
宫群章
韩璞
王五奇
焦海亮
黄林
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
China Construction Seventh Engineering Division Corp Ltd
China Construction Seventh Engineering Bureau Installation Engineering Co Ltd
Original Assignee
China Construction Seventh Engineering Division Corp Ltd
China Construction Seventh Engineering Bureau Installation Engineering Co Ltd
Priority date (The priority date 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 date listed.)
Filing date
Publication date
Application filed by China Construction Seventh Engineering Division Corp Ltd, China Construction Seventh Engineering Bureau Installation Engineering Co Ltd filed Critical China Construction Seventh Engineering Division Corp Ltd
Priority to CNU200720091084XU priority Critical patent/CN201073590Y/en
Application granted granted Critical
Publication of CN201073590Y publication Critical patent/CN201073590Y/en
Anticipated expiration legal-status Critical
Expired - Fee Related legal-status Critical Current

Links

Images

Landscapes

  • Treating Waste Gases (AREA)

Abstract

The utility model discloses a flue gas desulfurization absorber tower, comprising a tower drum and a tower cover. A slurry circulating tank, an inlet of flue gas, a region of oxidation reaction, a spray level, a demister and a outlet of flue gas on the top of the tower drum are arranged successively in the tower drum from down to up, the spray level comprises a main pipe and a branch pipe, the branch pipe is laterally arranged on the main pipe, a nozzle is arranged on the branch pipe, a inlet of circulating slurry is arranged on the position of the tower drum corresponding to the main pipe of the spray level, a stainless steel mesh filter screen is arranged at the inlet of circulating slurry, the inlet of circulating slurry and the main pipe of the spray level are connected with each other; the demister is a two-level demister, the second order demister is on the first order demister, a cleanup spray nozzle is arranged at each demister, two non-metallic expansion joints are arranged respectively at the inlet of flue gas and the outlet of flue gas. The flue gas desulfurization absorber tower has the advantages of high desulfurization efficiency, little dosage of absorbent namely limestone, high equipment running efficiency, reducing production cost. The utility model is good equipment in the wet limestone-gypsum fuel gas desulfurization system for boiler flue gas, and is suitable for extension and application.

Description

烟气脱硫吸收塔 Flue gas desulfurization absorption tower

技术领域 technical field

本实用新型属于环保设备的技术领域,具体涉及烟气脱硫吸收塔。The utility model belongs to the technical field of environmental protection equipment, in particular to a flue gas desulfurization absorption tower.

背景技术 Background technique

近年来,集除尘、冷却、吸收、氧化功能为一体的单塔式湿法烟气脱硫装置已得到广泛应用,但是目前的吸收塔的脱硫效率不高,吸收剂即石灰石的用量较大,而且设备的运转率低。In recent years, a single-tower wet flue gas desulfurization device integrating dust removal, cooling, absorption, and oxidation has been widely used, but the desulfurization efficiency of the current absorption tower is not high, and the amount of absorbent, namely limestone, is relatively large, and The operating rate of the equipment is low.

实用新型内容Utility model content

本实用新型的目的是提供一种烟气脱硫吸收塔,利用此装置可以提高吸收塔脱硫效率,减少吸收剂的用量,并且能提高设备的运转率,降低了生产成本。The purpose of this utility model is to provide a flue gas desulfurization absorption tower, which can improve the desulfurization efficiency of the absorption tower, reduce the amount of absorbent, improve the operation rate of the equipment, and reduce the production cost.

本实用新型所采用的技术方案是:烟气脱硫吸收塔,由塔筒和与塔筒相配装的塔盖构成,所述的塔筒内部从下向上依次为循环浆液池、氧化反应区、喷淋层、除雾器和塔筒顶部的烟气出口,其中塔筒的循环浆液池下部一侧设石灰石浆液入口和氧化空气入口,氧化空气入口在石灰石浆液入口上方,塔筒的循环浆液池下部另一侧设循环浆液出口和石膏浆液出口,石膏浆液出口在循环浆液出口的上方,所述的喷淋层包括母管和支管,支管侧向设在母管上,喷嘴设在支管上,塔筒与喷淋层的母管对应的位置上设循环浆液入口,循环浆液入口处设有不锈钢网格状滤网,循环浆液入口与喷淋层的母管相通;所述的除雾器为两级除雾器,二级除雾器在一级除雾器的上面,一级除雾器的上层设下喷的清洗喷嘴,下层设有上喷的清洗喷嘴,二级除雾器的上层设下喷的清洗喷嘴,下层设有上喷的清洗喷嘴,除雾器对应的塔筒上设有清洗水入口,清洗水入口与清洗喷嘴相通;在氧化区和喷淋层之间设烟气入口;在烟气入口和烟气出口分别设有非金属膨胀节。The technical scheme adopted in the utility model is: the flue gas desulfurization absorption tower is composed of a tower tube and a tower cover matched with the tower tube. The flue gas outlet at the top of the spray layer, demister and tower tube, where the lower side of the circulating slurry tank of the tower tube is provided with a limestone slurry inlet and an oxidation air inlet, the oxidation air inlet is above the limestone slurry inlet, and the lower part of the circulating slurry tank of the tower tube The other side is provided with a circulating slurry outlet and a gypsum slurry outlet. The gypsum slurry outlet is above the circulating slurry outlet. The spray layer includes a main pipe and a branch pipe. The cylinder and the main pipe of the spray layer are provided with a circulating slurry inlet, and a stainless steel mesh filter is arranged at the circulating slurry inlet, and the circulating slurry inlet is communicated with the main pipe of the spray layer; the demister is two The first-level demister, the second-level demister is above the first-level demister. Cleaning nozzles for downward spraying, cleaning nozzles for upward spraying on the lower layer, and cleaning water inlets on the tower corresponding to the demister, which are connected to the cleaning nozzles; flue gas inlets are set between the oxidation zone and the spray layer ; There are non-metallic expansion joints at the flue gas inlet and flue gas outlet respectively.

上述的烟气脱硫吸收塔,所述的喷淋层至少三层,并且相互差开距离叠加,每两层母管形成一夹角,每层喷淋层塔筒对应母管的位置上都设循环浆液入口。In the above-mentioned flue gas desulfurization absorption tower, the spray layers are at least three layers, and they are superimposed with different distances from each other. Every two layers of main pipes form an angle, and each spray layer is provided at the position corresponding to the main pipes. Circulation slurry inlet.

上述的烟气脱硫吸收塔,除雾器也可以为Z字型。In the above-mentioned flue gas desulfurization absorption tower, the mist eliminator can also be Z-shaped.

上述的烟气脱硫吸收塔,除雾器也可以为水平型。The above-mentioned flue gas desulfurization absorption tower and demister can also be horizontal.

上述的烟气脱硫吸收塔,除雾器也可以为人字型。In the above-mentioned flue gas desulfurization absorption tower, the mist eliminator can also be herringbone.

上述的烟气脱硫吸收塔,除雾器也可以为菱型。In the above-mentioned flue gas desulfurization absorption tower, the mist eliminator can also be rhombic.

上述的烟气脱硫吸收塔,除雾器还可以为X字型。In the above-mentioned flue gas desulfurization absorption tower, the mist eliminator can also be X-shaped.

本实用新型的有益效果:烟气脱硫吸收塔的脱硫效率高,吸收剂即石灰石的用量少,而且设备的运转率高,降低了生产成本,是锅炉尾气石灰石-石膏湿法烟气脱硫系统中不可多得的装置,适合推广应用。The beneficial effects of the utility model: the desulfurization efficiency of the flue gas desulfurization absorption tower is high, the amount of absorbent, that is, limestone is small, and the operation rate of the equipment is high, which reduces the production cost. It is a boiler tail gas limestone-gypsum wet flue gas desulfurization system A rare device in China, suitable for popularization and application.

附图说明 Description of drawings

图1是本实用新型结构示意图Fig. 1 is a structural representation of the utility model

图2是本实用新型喷淋层俯视图Figure 2 is a top view of the spray layer of the utility model

图3是本实用新型除雾器俯视图Figure 3 is a top view of the utility model demister

图4是本实用新型除雾器A-A向剖示图Figure 4 is a sectional view of the utility model demister A-A

图5是本实用新型除雾器另一种方式的A-A向剖示图Fig. 5 is an A-A sectional view of another mode of the mist eliminator of the present invention

图6是本实用新型除雾器另一种方式的A-A向剖示图Fig. 6 is an A-A sectional view of another mode of the mist eliminator of the present invention

图7是本实用新型除雾器另一种方式的A-A向剖示图Fig. 7 is an A-A sectional view of another mode of the mist eliminator of the present invention

图8是本实用新型除雾器另一种方式的A-A向剖示图Fig. 8 is an A-A sectional view of another mode of the mist eliminator of the present invention

图9是本实用新型除雾器另一种方式的A-A向剖示图Fig. 9 is an A-A sectional view of another mode of the mist eliminator of the present invention

具体实施方式 Detailed ways

如图1所示烟气脱硫吸收塔,由塔筒和与塔筒相配装的塔盖7构成,所述的塔筒内部从下向上依次为循环浆液池1、氧化反应区6、喷淋层2、除雾器3和塔筒顶部的烟气出口4,其中塔筒的循环浆液池下部一侧设石灰石浆液入口1.1和氧化空气入口1.2,氧化空气入口在石灰石浆液入口上方,塔筒的循环浆液池下部另一侧设循环浆液出口1.3和石膏浆液出口1.4,石膏浆液出口在循环浆液出口的上方,所述的喷淋层包括母管2.1和支管2.2,支管2.2侧向设在母管2.1上,喷嘴2.3设在支管上,塔筒与喷淋层的母管2.1对应的位置上设循环浆液入口8,循环浆液入口8与喷淋层的母管2.1相通,循环浆液经过喷淋层喷嘴2.3后形成细化喷雾,喷射到氧化反应区6,使烟气被迅速冷却达到饱和,循环浆液中的CaCO3与烟气中的SO2、SO3、HCl和HF等有害物质发生化学反应,生成的CaSO4和CaSO3及未完全反应的浆液流回到循环浆液池,浆液在循环浆液泵的作用下循环使用;循环浆液入口处设有不锈钢网格状滤网,循环浆液入口处的不锈钢网格状滤网可以防止塔内沉淀物吸入泵体造成泵的堵塞或损坏及喷嘴的堵塞;所述的除雾器3为两级除雾器,二级除雾器在一级除雾器的上面,烟气携带着液滴经过一级除雾器时,液滴由于惯性作用,留在一级除雾器上,初次除雾的烟气再经过二级除雾可以达到更好的除雾效果,一级除雾器的上层设下喷的清洗喷嘴3.1,下层设有上喷的清洗喷嘴3.2,二级除雾器的上层设下喷的清洗喷嘴3.3,下层设有上喷的清洗喷嘴3.4,除雾器对应的塔筒上设有清洗水入口10,每个清洗喷嘴与清洗水入口相通,清洗水由除雾器清洗系统提供,除雾器清洗系统装在吸收塔外部,清洗系统采用自动控制,清洗系统间断运行,清洗水从喷嘴强力喷向除雾器元件,带走除雾器顺流面和逆流面上的固体颗粒,同时清洗水还用于补充吸收塔中的水分损失;在氧化区和喷淋层之间设烟气入口5;在烟气入口5处设有非金属膨胀节9.1,烟气出口设有非金属膨胀节9.2,所设的非金属膨胀节用来补偿由于温度变化引起的烟道纵向变形。As shown in Figure 1, the flue gas desulfurization absorption tower is composed of a tower tube and a tower cover 7 matched with the tower tube. The interior of the tower tube is sequentially composed of a circulating slurry pool 1, an oxidation reaction zone 6, and a spray layer from bottom to top. 2. The demister 3 and the flue gas outlet 4 at the top of the tower, wherein the lower side of the circulating slurry pool of the tower is provided with a limestone slurry inlet 1.1 and an oxidation air inlet 1.2, and the oxidation air inlet is above the limestone slurry inlet. The circulation of the tower The other side of the lower part of the slurry tank is provided with a circulating slurry outlet 1.3 and a gypsum slurry outlet 1.4, the gypsum slurry outlet is above the circulating slurry outlet, the spray layer includes a main pipe 2.1 and a branch pipe 2.2, and the branch pipe 2.2 is arranged laterally on the main pipe 2.1 On the top, the nozzle 2.3 is set on the branch pipe, and the position corresponding to the main pipe 2.1 of the spray layer is provided with a circulating slurry inlet 8. The circulating slurry inlet 8 communicates with the main pipe 2.1 of the spray layer, and the circulating slurry passes through the nozzle of the spray layer After 2.3, a fine spray is formed and sprayed into the oxidation reaction zone 6, so that the flue gas is rapidly cooled to saturation, and the CaCO 3 in the circulating slurry chemically reacts with harmful substances such as SO 2 , SO 3 , HCl and HF in the flue gas, The generated CaSO 4 and CaSO 3 and the incompletely reacted slurry flow back to the circulating slurry tank, and the slurry is recycled under the action of the circulating slurry pump; a stainless steel mesh filter is installed at the inlet of the circulating slurry, and the stainless steel mesh at the inlet of the circulating slurry The grid-like filter screen can prevent the sediment in the tower from being sucked into the pump body to cause blockage or damage of the pump and blockage of the nozzle; When the flue gas carries liquid droplets through the first-level demister, the liquid droplets remain on the first-level demister due to inertia, and the first-stage demistered flue gas can then pass through the second-level demister to achieve better demisting. Fog effect, the upper layer of the primary demister is equipped with cleaning nozzle 3.1 for the lower spray, the lower layer is equipped with the cleaning nozzle 3.2 for the upper spray, the upper layer of the second-level demister is equipped with the cleaning nozzle 3.3 for the lower spray, and the lower layer is equipped with the cleaning nozzle for the upper spray Nozzle 3.4, the tower corresponding to the demister is provided with a cleaning water inlet 10, and each cleaning nozzle is connected to the cleaning water inlet, and the cleaning water is provided by the demister cleaning system, which is installed outside the absorption tower to clean The system adopts automatic control, and the cleaning system operates intermittently. The cleaning water is sprayed from the nozzle to the demister element, taking away the solid particles on the downstream and countercurrent surfaces of the demister, and the cleaning water is also used to supplement the water in the absorption tower. Loss; a flue gas inlet 5 is set between the oxidation zone and the spray layer; a non-metallic expansion joint 9.1 is set at the flue gas entrance 5, and a non-metallic expansion joint 9.2 is set at the flue gas outlet. To compensate for the longitudinal deformation of the flue due to temperature changes.

上述的烟气脱硫吸收塔,所述的喷淋层至少三层,并且相互差开距离叠加,每两层母管形成一夹角,每层喷淋层塔筒对应母管的位置上都设循环浆液入口,经过一层喷淋层脱硫的烟气继续上升,到达上层喷淋层,烟气与上层喷淋层来的浆液相互作用发生化学反应,使得SO2和SO3得最大程度的吸收。In the above-mentioned flue gas desulfurization absorption tower, the spray layers are at least three layers, and they are superimposed with different distances from each other. Every two layers of main pipes form an angle, and each spray layer is provided at the position corresponding to the main pipes. At the inlet of the circulating slurry, the flue gas desulfurized by a spray layer continues to rise and reaches the upper spray layer. The flue gas interacts with the slurry from the upper spray layer to undergo a chemical reaction, so that SO 2 and SO 3 can be absorbed to the greatest extent. .

上述的烟气脱硫吸收塔,所述的除雾器如图4所示为Z字型,烟气进入Z字形除雾器由于通道的偏折,液滴撞击在除雾器上被收集,在惯性的作用下实现气液分离,除去液滴的净化烟气继续上升进入烟囱排入大气。In the above-mentioned flue gas desulfurization absorption tower, the demister is Z-shaped as shown in Figure 4, and the flue gas enters the Z-shaped demister due to the deflection of the channel, and the liquid droplets hit the demister and are collected. The gas-liquid separation is realized under the action of inertia, and the purified flue gas after removing the liquid droplets continues to rise into the chimney and be discharged into the atmosphere.

上述的烟气脱硫吸收塔,其中除雾器也可以用如图5所示为水平型。In the above-mentioned flue gas desulfurization absorption tower, the mist eliminator can also be used as a horizontal type as shown in Figure 5 .

上述的烟气脱硫吸收塔,其中除雾器也可以用如图6和图7所示人字型。In the above-mentioned flue gas desulfurization absorption tower, the mist eliminator can also be herringbone as shown in Fig. 6 and Fig. 7 .

上述的烟气脱硫吸收塔,其中除雾器也可以用如图8所示为菱型。In the above-mentioned flue gas desulfurization absorption tower, the demister can also be used as a rhombus as shown in Figure 8 .

上述的烟气脱硫吸收塔,其中除雾器还可以用如图9所示X字型。In the above-mentioned flue gas desulfurization absorption tower, the mist eliminator can also be in an X shape as shown in Figure 9 .

本实用新型的工作过程:锅炉烟气经过除尘器除尘、热交换器降温和增压风机增压后进入烟气脱硫吸收塔。烟气首先进入塔下部的氧化反应区6,循环浆液池1的循环浆液由循环浆液泵抽出进入到喷淋层2后通过喷嘴2.3喷射到氧化反应区,烟气被迅速冷却达到饱和,浆液中的CaCO3与烟气中的SO2、SO3、HCl和HF等有害物质发生化学反应,生成的CaSO4和CaSO3及未完全反应的浆液流回到循环浆液池,浆液在循环浆液泵的作用下循环使用。烟气继续上升,到达上层喷淋层,烟气流速发生变化,与上层喷淋层来的浆液相互作用,产生气液湍流扩散,化学反应明显加快,SO2和SO3得到进一步吸收,生成的CaSO4和CaSO3及未完全反应的浆液流回到循环浆液池,烟气继续上升,到达上层喷淋层,烟气与上层喷淋层来的浆液相互作用发生化学反应,SO2和SO3得最大程度的吸收;循环浆液池里循环浆液里的CaSO3在氧化空气的作用下发生完全反应生成CaSO4,CaSO4在石膏浆液泵的作用下送至石膏脱水装置。完成脱硫过程的烟气到达除雾器3,除雾器为Z字形,烟气进入Z字形除雾器由于通道的偏折,液滴撞击在除雾器上被收集,在惯性的作用下实现气液分离,除去液滴的净化烟气继续上升进入烟囱排入大气。The working process of the utility model: the boiler flue gas enters the flue gas desulfurization absorption tower after being dedusted by the dust collector, cooled by the heat exchanger and boosted by the booster fan. The flue gas first enters the oxidation reaction zone 6 at the lower part of the tower, and the circulating slurry in the circulating slurry tank 1 is pumped out by the circulating slurry pump and enters the spray layer 2, and then sprayed into the oxidation reaction zone through the nozzle 2.3, the flue gas is rapidly cooled to saturation, and the slurry in the slurry CaCO 3 chemically reacts with harmful substances such as SO 2 , SO 3 , HCl and HF in the flue gas, and the generated CaSO 4 and CaSO 3 and the incompletely reacted slurry flow back to the circulating slurry pool, and the slurry is in the circulating slurry pump. Under the effect of recycling. The flue gas continues to rise and reaches the upper spray layer, the flow velocity of the flue gas changes, interacts with the slurry from the upper spray layer, produces gas-liquid turbulent diffusion, and the chemical reaction is significantly accelerated, SO 2 and SO 3 are further absorbed, and the generated CaSO 4 and CaSO 3 and the incompletely reacted slurry flow back to the circulating slurry tank, the flue gas continues to rise and reaches the upper spray layer, and the flue gas interacts with the slurry from the upper spray layer to undergo a chemical reaction, SO 2 and SO 3 The CaSO 3 in the circulating slurry in the circulating slurry pool reacts completely under the action of oxidizing air to form CaSO 4 , and the CaSO 4 is sent to the gypsum dehydration device under the action of the gypsum slurry pump. The flue gas that has completed the desulfurization process reaches the demister 3, which is in a zigzag shape, and the flue gas enters the zigzag demister. Due to the deflection of the channel, the liquid droplets hit the demister and are collected, which is realized under the action of inertia. The gas and liquid are separated, and the purified flue gas that removes the liquid droplets continues to rise into the chimney and be discharged into the atmosphere.

Claims (7)

1. fume desulfurating absorption tower, by the tower tube with constitute with the equipped mutually tower lid of tower tube, tower tube inside is followed successively by the recycle slurry liquid pool from bottom to top, oxidation reaction zone, spraying layer, the exhanst gas outlet at demister and tower tube top, recycle slurry liquid pool bottom one side of described tower tube is established lime stone slurry inlet and oxidation air inlet, the oxidation air inlet is above the lime stone slurry inlet, the recycle slurry liquid pool bottom opposite side of tower tube is established loop slurry outlet and gypsum slurries outlet, the gypsum slurries outlet is below the loop slurry outlet, it is characterized in that: described spraying layer comprises female pipe and arm, the arm side direction is located on female pipe, nozzle is located on the arm, the tower tube is managed with the mother of spraying layer and is established the loop slurry inlet on the corresponding position, the loop slurry porch is provided with stainless (steel) wire trellis filter screen, and the loop slurry inlet communicates with female pipe of spraying layer; Described demister is the two-stage demister, the secondary demister is on the one-level demister, the upper strata of one-level demister is provided with down the washer jet of spray, lower floor is provided with the washer jet of spray, the upper strata of secondary demister is provided with down the washer jet of spray, lower floor is provided with the washer jet of spray, and the tower tube of demister correspondence is provided with the rinse water inlet, and the rinse water inlet communicates with washer jet; Between zoneofoxidation and spraying layer, establish smoke inlet; Be respectively equipped with non-metal expansion joint at smoke inlet and exhanst gas outlet.
2. fume desulfurating absorption tower according to claim 1 is characterized in that: at least three layers of described spraying layers, and the phase mutual deviation opens distance stack, tubular the having angle of every two-layer mother, and every layer of spraying layer tower tube position corresponding with female pipe all established loop slurry and entered the mouth.
3. fume desulfurating absorption tower according to claim 2 is characterized in that: described demister is the Z font.
4. fume desulfurating absorption tower according to claim 2 is characterized in that: described demister is a horizontal type.
5. fume desulfurating absorption tower according to claim 2 is characterized in that: described demister is chevron shaped.
6. fume desulfurating absorption tower according to claim 2 is characterized in that: described demister is a diamond pattern.
7. fume desulfurating absorption tower according to claim 2 is characterized in that: described demister is the X font.
CNU200720091084XU 2007-07-18 2007-07-18 Absorbing tower with flue gas desulfurization Expired - Fee Related CN201073590Y (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CNU200720091084XU CN201073590Y (en) 2007-07-18 2007-07-18 Absorbing tower with flue gas desulfurization

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CNU200720091084XU CN201073590Y (en) 2007-07-18 2007-07-18 Absorbing tower with flue gas desulfurization

Publications (1)

Publication Number Publication Date
CN201073590Y true CN201073590Y (en) 2008-06-18

Family

ID=39518853

Family Applications (1)

Application Number Title Priority Date Filing Date
CNU200720091084XU Expired - Fee Related CN201073590Y (en) 2007-07-18 2007-07-18 Absorbing tower with flue gas desulfurization

Country Status (1)

Country Link
CN (1) CN201073590Y (en)

Cited By (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN104941380A (en) * 2014-03-31 2015-09-30 英尼奥斯欧洲股份公司 Improved smog eliminator operation for quenching effluent
CN104998535A (en) * 2014-04-22 2015-10-28 上海映特环保技术有限公司 Double-effect flue gas purification apparatus and purification method thereof
CN106807162A (en) * 2017-03-28 2017-06-09 金华三鼎环保机械有限公司 A kind of paint mist treatment device
CN107803101A (en) * 2017-10-31 2018-03-16 中国三冶集团有限公司宁波分公司 The manufacturing process of fume desulfurating absorption tower structure and absorption tower body
CN112221341A (en) * 2020-10-28 2021-01-15 宁夏和兴碳基材料有限公司 A high-efficient desulfurization absorption tower for industrial flue gas
CN113018991A (en) * 2021-03-29 2021-06-25 中国华电科工集团有限公司 Desulfurization absorption tower with forced cyclone separation device

Cited By (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN104941380A (en) * 2014-03-31 2015-09-30 英尼奥斯欧洲股份公司 Improved smog eliminator operation for quenching effluent
TWI666056B (en) * 2014-03-31 2019-07-21 瑞士商億諾斯歐洲公司 Improved mist eliminator operation for quench effluent
CN104998535A (en) * 2014-04-22 2015-10-28 上海映特环保技术有限公司 Double-effect flue gas purification apparatus and purification method thereof
CN106807162A (en) * 2017-03-28 2017-06-09 金华三鼎环保机械有限公司 A kind of paint mist treatment device
CN107803101A (en) * 2017-10-31 2018-03-16 中国三冶集团有限公司宁波分公司 The manufacturing process of fume desulfurating absorption tower structure and absorption tower body
CN107803101B (en) * 2017-10-31 2019-10-01 中国三冶集团有限公司宁波分公司 The manufacturing process of fume desulfurating absorption tower structure and absorption tower ontology
CN112221341A (en) * 2020-10-28 2021-01-15 宁夏和兴碳基材料有限公司 A high-efficient desulfurization absorption tower for industrial flue gas
CN113018991A (en) * 2021-03-29 2021-06-25 中国华电科工集团有限公司 Desulfurization absorption tower with forced cyclone separation device

Similar Documents

Publication Publication Date Title
CN102974185B (en) Modularized integrated smoke purification system and method for removing plurality of pollutants
CN102343215B (en) Dual-chamber multi-absorption wet flue gas desulfurizing device
CN201073590Y (en) Absorbing tower with flue gas desulfurization
CN104607021B (en) Double-circulating flue gas dust removal desulfurization tower and flue gas desulfurization method
CN104258668B (en) A kind of washing degree of depth dust arrester
CN108786398A (en) Flue gas desulfurization regenerates integrated tower and Regeneratable wet fuel gas desulfurizing method
CN204637975U (en) Flue gas desulfurization enhancing device
CN103120894A (en) Desulfurizing absorption tower
CN112933839A (en) Spiral demisting and dedusting device with double diversion grooves
CN204182256U (en) A kind of washing degree of depth dust arrester
CN208711402U (en) A high-efficiency multi-stage spray foam dust removal and desulfurization device
CN108744941A (en) A kind of the spray column desulphurization system and method for high-order arrangement
CN205850533U (en) A kind of washing absorption tower
CN205988672U (en) A kind of processing meanss smelting spuious flue gas
CN205925276U (en) No pump cascade filter chamber
CN208626955U (en) Flue gas scrubbing system
CN208302457U (en) Wet scrubber tower high-efficiency demisting apparatus
CN207980838U (en) A kind of reciprocating two-region spray absorber
CN207042235U (en) A kind of flue-gas dust-removing and desulfurization device
CN205360936U (en) A condensing takes off dirt defogging device for wet flue gas desulfurization system
CN203090739U (en) Desulfurization absorption tower
CN103977696A (en) Spray absorption tower suitable for coal-fired boiler flue gas desulfurization and denitrification
CN212819076U (en) System for flue gas pollutant degree of depth desorption
CN102649026A (en) Dry dust removal and wet desulphurization integral efficient smoke gas purification device
CN201692760U (en) Gas-liquid swirling-flow desulfuration dust cleaner of efficient desulfuration dust-cleaning device

Legal Events

Date Code Title Description
C14 Grant of patent or utility model
GR01 Patent grant
CF01 Termination of patent right due to non-payment of annual fee

Granted publication date: 20080618

Termination date: 20160718

CF01 Termination of patent right due to non-payment of annual fee