CN204502785U - A kind of flue gas device for deep cleaning for efficient desulfurizing and dust collecting - Google Patents

A kind of flue gas device for deep cleaning for efficient desulfurizing and dust collecting Download PDF

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CN204502785U
CN204502785U CN201520156073.XU CN201520156073U CN204502785U CN 204502785 U CN204502785 U CN 204502785U CN 201520156073 U CN201520156073 U CN 201520156073U CN 204502785 U CN204502785 U CN 204502785U
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slurry
flue gas
absorption
absorption area
spraying layer
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龚蔚成
冯延林
谢光辉
李蓉
姚超良
黄黎明
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YONKER ENVIRONMENTAL PROTECTION CO Ltd
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Abstract

本实用新型涉及一种用于高效脱硫除尘的烟气深度净化装置,包括吸收塔,吸收塔内设浆液池和位于浆液池上方的烟气吸收区,在烟气入口处设循环浆液喷淋装置,用隔板将烟气吸收区隔成第一吸收区与位于第一吸收区一侧的第二吸收区,隔板与浆液池之间设由第一吸收区流向第二吸收区的烟气折返通道,第一吸收区设第一浆液喷淋层,第二吸收区设第二浆液喷淋层,第一浆液喷淋层、第二浆液喷淋层和循环浆液喷淋装置均通过浆液循环泵与浆液池连接,第二浆液喷淋层上方自下至上依次设除雾器、除尘器和烟气出口。该装置在一个设备内同步实现了烟气脱硫除尘的深度净化,降低了吸收塔的高度,减少了烟气流动的阻力,节约了建造费用,降低了其运行成本。

The utility model relates to a flue gas deep purification device for high-efficiency desulfurization and dust removal, comprising an absorption tower, a slurry pool and a flue gas absorption area above the slurry pool are arranged in the absorption tower, and a circulating slurry spray device is arranged at the flue gas inlet The flue gas absorption area is divided into the first absorption area and the second absorption area located on the side of the first absorption area with a partition, and the flue gas flowing from the first absorption area to the second absorption area is set between the partition and the slurry pool. Channel, the first slurry spraying layer is set in the first absorption area, the second slurry spraying layer is set in the second absorption area, the first slurry spraying layer, the second slurry spraying layer and the circulating slurry spraying device are all passed through the slurry circulating pump It is connected with the slurry tank, and above the second slurry spray layer, a mist eliminator, a dust collector and a flue gas outlet are arranged in sequence from bottom to top. The device simultaneously realizes the deep purification of flue gas desulfurization and dust removal in one device, reduces the height of the absorption tower, reduces the resistance of flue gas flow, saves construction costs and reduces its operating costs.

Description

一种用于高效脱硫除尘的烟气深度净化装置A flue gas deep purification device for efficient desulfurization and dust removal

技术领域 technical field

本实用新型涉及一种用于脱硫除尘的烟气深度净化装置。 The utility model relates to a flue gas deep purification device for desulfurization and dust removal.

背景技术 Background technique

随着我国经济的发展,环境污染也日益严重,大面积雾霾天气时有发生,为了改善环境,目前,国际和国内烟气脱硫工艺80%以上采用石灰石—石膏湿法脱硫工艺,烟气石灰石—石膏湿法脱硫工艺一般采用单个吸收塔,随着环保要求的不断提高,在我国要求经济发达地区及一些城市群的燃煤电厂烟气中污染物排放限值达到燃气轮机组的排放要求,即所谓的“超洁净排放”,要求排放烟气中NOx浓度≤50mg/Nm3,SO2浓度≤35mg/Nm3,烟尘浓度≤5mg/Nm3。根据这一新的要求,许多燃煤电厂实际脱硫效率应达到99%以上,采用过去的单塔工艺已经难以满足这一新要求。因此,现在出现了双塔双循环工艺和单塔双循环工艺。其中双塔双循环工艺就是将两个吸收塔串联,在第二个吸收塔后加装湿式电除尘器的工艺,此工艺烟道复杂,烟气阻力大,占地面积大,运行电耗高。单塔双循环工艺其实是双塔双循环的一个变异,就是将两个塔的喷淋层叠加上下布置,在塔与塔的喷淋层之间设接液托盘,使上一吸收塔的喷淋液不喷洒至下一吸收塔中,上部吸收塔的浆池布置在吸收塔外,此工艺的缺点是吸收塔很高,上面无法再加装湿式电除尘器,湿式电除尘器只能水平布置,增加了烟道的复杂程度,加大了烟气阻力,有两个浆液池,运行控制复杂,运行费用高,投资费用高。 With the development of China's economy, environmental pollution is becoming more and more serious, and large-scale haze weather occurs from time to time. In order to improve the environment, at present, more than 80% of international and domestic flue gas desulfurization processes use limestone-gypsum wet desulfurization process, flue gas limestone ——The gypsum wet desulfurization process generally adopts a single absorption tower. With the continuous improvement of environmental protection requirements, the emission limit of pollutants in the flue gas of coal-fired power plants in economically developed areas and some urban agglomerations in China is required to meet the emission requirements of gas turbine units, that is, The so-called "ultra-clean emission" requires that the NOx concentration in the exhaust gas be ≤50mg/Nm 3 , the SO 2 concentration be ≤35mg/Nm 3 , and the soot concentration be ≤5mg/Nm 3 . According to this new requirement, the actual desulfurization efficiency of many coal-fired power plants should reach more than 99%. It is already difficult to meet this new requirement with the single-tower process in the past. Therefore, there are now two-tower double-cycle processes and single-tower double-cycle processes. Among them, the double-tower double-circulation process is to connect two absorption towers in series and install a wet electrostatic precipitator behind the second absorption tower. This process has complex flue, large flue gas resistance, large floor space, and high power consumption for operation. . The single-tower double-circulation process is actually a variation of the double-tower double-circulation process, that is, the spray layers of the two towers are superimposed and arranged up and down, and a liquid-receiving tray is set between the spray layers of the tower and the tower to make the spray of the previous absorption tower The shower liquid is not sprayed into the next absorption tower, and the slurry pool of the upper absorption tower is arranged outside the absorption tower. The disadvantage of this process is that the absorption tower is very high, and the wet electrostatic precipitator cannot be installed on it, and the wet electrostatic precipitator can only be horizontal. The layout increases the complexity of the flue and increases the resistance of the flue gas. There are two slurry tanks, the operation control is complicated, the operation cost is high, and the investment cost is high.

实用新型内容 Utility model content

本实用新型解决的技术问题是,简化脱硫除尘的烟气处理装置,使用一个烟气吸收塔可以同步实现烟气的双循环吸收、脱除微细颗粒烟尘、降低吸收塔的高度。 The technical problem solved by the utility model is to simplify the flue gas treatment device for desulfurization and dust removal, and use a flue gas absorption tower to simultaneously realize double-cycle absorption of flue gas, remove fine particle dust, and reduce the height of the absorption tower.

本实用新型的技术方案是,提供一种用于脱硫除尘的烟气处理装置,包括吸收塔,吸收塔内设浆液池和位于浆液池上方的烟气吸收区,在烟气入口处设循环浆液喷淋装置,用隔板将烟气吸收区隔成第一吸收区与位于第一吸收区一侧的第二吸收区,隔板与浆液池之间设由第一吸收区流向第二吸收区的烟气折返通道,第一吸收区设第一浆液喷淋层,第二吸收区设第二浆液喷淋层,第一浆液喷淋层、第二浆液喷淋层和循环浆液喷淋装置均通过浆液循环泵与浆液池连接,第二浆液喷淋层上方自下至上依次设除雾器、除尘器和烟气出口。 The technical scheme of the utility model is to provide a flue gas treatment device for desulfurization and dust removal, including an absorption tower, a slurry pool and a flue gas absorption area above the slurry pool are arranged in the absorption tower, and a circulating slurry is arranged at the flue gas inlet. The spray device uses a partition to divide the smoke absorption area into the first absorption area and the second absorption area located on the side of the first absorption area. The flue gas return channel, the first slurry spraying layer is set in the first absorption area, the second slurry spraying layer is set in the second absorption area, the first slurry spraying layer, the second slurry spraying layer and the circulating slurry spraying device all pass through The slurry circulation pump is connected with the slurry pool, and the mist eliminator, dust collector and flue gas outlet are arranged sequentially above the second slurry spray layer from bottom to top.

进一步地,在烟气入口处还设有冷却喷淋保护装置,冷却喷淋保护装置与通过自动控制阀水源连接;在浆液循环泵与循环浆液喷淋装置之间设流量检测仪,流量检测仪与自动控制阀连接。 Further, a cooling spray protection device is also provided at the entrance of the flue gas, and the cooling spray protection device is connected to the water source through the automatic control valve; a flow detector is installed between the slurry circulating pump and the circulating slurry spray device, and the flow detector Connect with automatic control valve.

进一步地,所述浆液池中设搅拌装置和氧化空气布气装置。 Further, a stirring device and an oxidizing air distribution device are installed in the slurry pool.

进一步地,所述除尘器为湿式电除尘器。 Further, the dust collector is a wet electrostatic precipitator.

进一步地,所述烟气出口的位置高于所述烟气入口的位置。 Further, the position of the flue gas outlet is higher than the position of the flue gas inlet.

进一步地,所述吸收塔的内壁设衬胶或衬玻璃鳞片防腐层。 Further, the inner wall of the absorption tower is provided with a rubber-lined or glass flake-lined anti-corrosion layer.

烟气从烟气入口进入,首先经循环浆液喷淋装置(包括喷淋管道、喷嘴)喷洒浆液使烟气降温冷却;当循环浆液喷淋装置或与其连接的浆液循环泵发生故障时,由冷却喷淋保护装置喷洒水使烟气降温冷却,冷却喷淋保护装置与常备水源相连,在水源管路上装有自动控制阀;自动控制阀与流量检测仪,流量检测仪能在检测到循环浆液喷淋装置没有浆液流动时使自动控制阀打开,冷却喷淋保护装置向入口烟气喷洒水降温以保护吸收塔内衬和浆液喷淋层;烟气进入第一吸收区后,自上向下流动,经第一浆液喷淋层喷洒浆液吸收烟气中的二氧化硫和粉尘;然后经烟气折返通道进入第二吸收区,自下向上流动,再经第二浆液喷淋层喷洒浆液进一步吸收烟气中的二氧化硫和粉尘,再经除雾器、除尘器、烟气出口排出。 The flue gas enters from the flue gas inlet, and first sprays the slurry through the circulating slurry spraying device (including spray pipes and nozzles) to cool down the flue gas; when the circulating slurry spraying device or the slurry circulation pump connected to it fails, the cooling system will The spray protection device sprays water to cool down the flue gas. The cooling spray protection device is connected to the standing water source, and an automatic control valve is installed on the water source pipeline; the automatic control valve and the flow detector, the flow detector can detect the circulating slurry spray When there is no slurry flow in the shower device, the automatic control valve is opened, and the cooling spray protection device sprays water to the inlet flue gas to cool down to protect the inner lining of the absorption tower and the slurry spray layer; after the flue gas enters the first absorption zone, it flows from top to bottom , spray the slurry through the first slurry spray layer to absorb sulfur dioxide and dust in the flue gas; then enter the second absorption zone through the flue gas return channel, flow from bottom to top, and then spray the slurry through the second slurry spray layer to further absorb the flue gas The sulfur dioxide and dust in the gas are discharged through the mist eliminator, dust collector and flue gas outlet.

湿式电除尘器直接安装于第一吸收区和第二吸收区上部,以下部的吸收塔作为支撑,从而解决现有直立式湿式电除尘器烟气流速比吸收塔内烟气流速慢而单个吸收塔顶安装位置不够的矛盾,对比安装于水平烟道上的湿式电除尘器此安装使烟道变得非常短、弯头少,不需要设计支架。 The wet electrostatic precipitator is directly installed on the upper part of the first absorption area and the second absorption area, supported by the lower absorption tower, so as to solve the problem that the flue gas velocity of the existing vertical wet electrostatic precipitator is slower than that in the absorption tower and the single absorption The installation position on the top of the tower is not enough. Compared with the wet electrostatic precipitator installed on the horizontal flue, this installation makes the flue very short, with few elbows, and no need to design brackets.

在吸收塔下部为浆液池,第一吸收区和第二吸收区共一个浆液池,浆液池中如同其他脱硫装置设计的一样,具有浆液搅拌装置和氧化空气布气装置等结构。 The lower part of the absorption tower is a slurry tank, the first absorption zone and the second absorption zone share a slurry tank, and the slurry tank is designed as other desulfurization devices, with structures such as a slurry stirring device and an oxidation air distribution device.

本装置用于烟气中二氧化硫、烟尘及其他PM2.5的脱除,烟气入口处二氧化硫含量在7000mg/Nm3,粉尘50 mg/Nm3时,通过该装置的处理能使二氧化硫的脱除率达到99.5%以上,出口SO2<35mg/Nm3,烟尘浓度<5mg/Nm3。该方法采用常用的石灰石—石膏湿法烟气脱硫,不同的是,该装置及方法采用包括两个吸收塔区域合为一个整体的吸收塔,单一浆池,实现脱硫效率99.5%以上,并且方便地集湿式电除尘器于一体。本装置提高了烟气脱硫除尘的效果,降低了吸收塔的高度,减少了烟气流动的阻力,节约了建设投资和装置运行成本。在节省能耗、节约场地、降低投资费用方面均优于现有的双塔双循环工艺或单塔双循环工艺等超洁净排放技术。 This device is used for the removal of sulfur dioxide, soot and other PM2.5 in the flue gas. When the sulfur dioxide content at the flue gas inlet is 7000 mg/Nm 3 and the dust is 50 mg/Nm 3 , the treatment of this device can make the removal of sulfur dioxide The efficiency reaches over 99.5%, the outlet SO 2 <35mg/Nm 3 , and the smoke concentration <5mg/Nm 3 . This method adopts the commonly used limestone-gypsum wet flue gas desulfurization method. The difference is that the device and method use an absorption tower including two absorption tower areas combined into one whole, and a single slurry tank to achieve a desulfurization efficiency of over 99.5%. Ground and wet electrostatic precipitator in one. The device improves the effect of flue gas desulfurization and dust removal, reduces the height of the absorption tower, reduces the resistance of flue gas flow, and saves construction investment and device operation cost. It is superior to the existing ultra-clean emission technologies such as double-tower double-cycle process or single-tower double-cycle process in terms of energy saving, site saving, and investment cost reduction.

附图说明 Description of drawings

图1表示本实用新型提供的烟气处理装置的结构原理示意图; Fig. 1 shows the schematic diagram of the structure and principle of the flue gas treatment device provided by the utility model;

图中1:烟气入口;2:循环浆液喷淋装置;3:第一浆液喷淋层;4:烟气折返通道;5:第二浆液喷淋层;6:浆液循环泵; 7:浆液池;8:除雾器;9:除尘器;10:水源;11:流量检测仪;12:自动控制阀;13:冷却喷淋保护装置;14:隔板;15:烟气出口。 In the figure 1: flue gas inlet; 2: circulating slurry spraying device; 3: first slurry spraying layer; 4: flue gas return channel; 5: second slurry spraying layer; 6: slurry circulating pump; 7: slurry pool; 8: mist eliminator; 9: dust collector; 10: water source; 11: flow detector; 12: automatic control valve; 13: cooling spray protection device; 14: clapboard; 15: flue gas outlet.

具体实施方式 Detailed ways

下面根据附图和实施例对本实用新型的进行详细说明。 The utility model is described in detail below according to the accompanying drawings and embodiments.

本实施例提供的烟气净化装置包括吸收塔,吸收塔内设浆液池7和位于浆液池7上方的烟气吸收区,在烟气入口1处设循环浆液喷淋装置2,用隔板14将烟气吸收区隔成第一吸收区与位于第一吸收区一侧的第二吸收区,隔板14与浆液池7之间设由第一吸收区流向第二吸收区的烟气折返通道4,第一吸收区设第一浆液喷淋层3,第二吸收区设第二浆液喷淋层5,第一浆液喷淋层3、第二浆液喷淋层5和循环浆液喷淋装置2均通过浆液循环泵6与浆液池7连接,第二浆液喷淋层5上方从下至上依次设除雾器8、除尘器9和烟气出口15。在烟气入口1处还设有冷却喷淋保护装置13,冷却喷淋保护装置13与通过自动控制阀12与水源10连接;在浆液循环泵6与循环浆液喷淋装置2之间设流量检测仪11,流量检测仪11与自动控制阀12连接。 The flue gas purification device provided in this embodiment includes an absorption tower, a slurry pool 7 and a flue gas absorption area located above the slurry pool 7 are arranged in the absorption tower, a circulating slurry spraying device 2 is set at the flue gas inlet 1, and a separator 14 The smoke absorption area is divided into the first absorption area and the second absorption area located on the side of the first absorption area, and the flue gas return channel flowing from the first absorption area to the second absorption area is set between the separator 14 and the slurry pool 7 4. Set the first slurry spray layer 3 in the first absorption zone, set the second slurry spray layer 5 in the second absorption zone, the first slurry spray layer 3, the second slurry spray layer 5 and the circulating slurry spray device 2 Both are connected to the slurry tank 7 through the slurry circulation pump 6, and the mist eliminator 8, the dust collector 9 and the flue gas outlet 15 are sequentially arranged above the second slurry spray layer 5 from bottom to top. A cooling spray protection device 13 is also provided at the flue gas inlet 1, and the cooling spray protection device 13 is connected to the water source 10 through the automatic control valve 12; a flow detection is set between the slurry circulating pump 6 and the circulating slurry spray device 2 Instrument 11, flow detector 11 is connected with automatic control valve 12.

待净化烟气从装置一侧顶部的烟气入口1进入烟气处理装置的吸收塔,入口处的烟道贴衬耐磨耐腐蚀的合金,在烟道入口处设有循环浆液喷淋装置2,使烟气降温以保护吸收塔内衬防腐材料和内部件不受到高温的冲击破坏同时对烟气进行初次洗涤。为节省投资,吸收塔内壁采用衬胶或衬玻璃鳞片进行防腐,浆液喷淋管道采用FRP材质,衬胶和衬玻璃鳞片材料其能承受的温度为90℃,FRP管道其所能承受的烟气温度为80℃,而烟气温度一般在100℃以上,入口段设循环喷淋装置2能将烟气温度降到70℃而不使上述材料被损环。为了防止烟道入口1内循环浆液喷淋装置2突然故障停止喷淋,在入口段循环喷淋装置2后装设冷却喷淋保护装置13,冷却喷淋保护装置13与常备水源10相连,在进水管道上装设自动控制阀12,当入口段循环喷淋装置正常运行时,自动控制阀12关闭,当循环喷淋装置2进水异常时,流量下降到设定值以下时,自动控制阀12开启,冷却喷淋保护装置13喷水对烟气喷雾降温。循环喷淋装置的进水管上装有流量检测仪11,流量检测仪11与自动控制阀12连接,控制自动控制阀12的开启和关闭。然后烟气进入烟气吸收区,烟气吸收区由隔板14分为左右两个吸收区域,分别为第一吸收区和第二吸收区,隔板14竖向设置或基本竖向设置,隔板下端不与浆液池7的液面接触而形成烟气折返通道;烟气经初步降温后先进入第一吸收区,自上向下流动,与第一吸收区中部设置的第一浆液喷淋层3喷出的浆液接触,烟气中的污染物SO2,粉尘、HCl、HF等被浆液洗涤,洗涤后的烟气继续下行,至塔底浆池液面后通过烟气折返通道4进入第二吸收区,烟气折返向上流,与第二吸收区中部设置的第二浆液喷淋层5喷出的浆液再一次接触,烟气中的污染物SO2,粉尘、HCl、HF等被浆液进一步洗涤脱除。洗涤后的烟气继续上升,通过上部设置的除雾器8,除去雾滴,再通过烟气流场调整段进入电除尘器9,捕集烟气中所带的微细粉尘和SO3等污染物后从烟气出口15排出。第一浆液喷淋层3和第二浆液喷淋层5喷洒的浆液均来自塔下部的公共浆液池7,与烟气接触洗涤完烟气中的污染物后又落入浆液池7,浆液池含大量石灰石和石膏溶液,浆液池7设有搅拌装置,防止石灰石和石膏沉淀;SO2被浆液吸收后溶解于水生成亚硫酸,向浆液池充入空气使亚硫酸氧化为硫酸,其与浆液中的碳酸钙反应生成石膏。 The flue gas to be purified enters the absorption tower of the flue gas treatment device from the flue gas inlet 1 at the top of the side of the device. The flue at the inlet is lined with wear-resistant and corrosion-resistant alloy, and a circulating slurry spray device 2 is installed at the flue inlet. , to cool down the flue gas to protect the anti-corrosion lining material and internal parts of the absorption tower from being damaged by the impact of high temperature, and at the same time to wash the flue gas for the first time. In order to save investment, the inner wall of the absorption tower is anti-corrosion with rubber lining or glass flake lining. The slurry spray pipe is made of FRP material. The rubber lining and glass flake lining material can withstand a temperature of 90 ° C. The flue gas that the FRP pipeline can withstand The temperature is 80°C, and the flue gas temperature is generally above 100°C. The inlet section is equipped with a circulating spray device 2, which can reduce the flue gas temperature to 70°C without damaging the above-mentioned materials. In order to prevent the sudden failure of the circulating slurry spraying device 2 in the flue inlet 1 and stop spraying, a cooling spraying protection device 13 is installed behind the circulating spraying device 2 in the inlet section, and the cooling spraying protection device 13 is connected to the standing water source 10. An automatic control valve 12 is installed on the water inlet pipe. When the circulation spraying device in the inlet section is in normal operation, the automatic control valve 12 is closed. 12 is opened, and the cooling spray protection device 13 sprays water to cool down the flue gas spray. A flow detector 11 is installed on the water inlet pipe of the circulating spray device, and the flow detector 11 is connected with the automatic control valve 12 to control the opening and closing of the automatic control valve 12. Then the flue gas enters the flue gas absorption area, which is divided into two left and right absorption areas by the partition plate 14, which are respectively the first absorption area and the second absorption area. The partition plate 14 is arranged vertically or substantially vertically. The lower end of the plate does not contact the liquid surface of the slurry pool 7 to form a flue gas return channel; the flue gas enters the first absorption zone after preliminary cooling, flows from top to bottom, and sprays with the first slurry set in the middle of the first absorption zone The slurry sprayed from layer 3 contacts, and the pollutants SO 2 , dust, HCl, HF, etc. in the flue gas are washed by the slurry, and the washed flue gas continues to descend, and enters through the flue gas return channel 4 after reaching the liquid level of the slurry pool at the bottom of the tower. In the second absorption zone, the flue gas turns back to flow upwards and contacts again with the slurry sprayed from the second slurry spray layer 5 in the middle of the second absorption zone, and the pollutants SO 2 , dust, HCl, HF, etc. in the flue gas are The slurry is further washed off. The washed flue gas continues to rise, passes through the mist eliminator 8 installed on the upper part to remove mist droplets, and then enters the electrostatic precipitator 9 through the flue gas flow field adjustment section to capture fine dust and SO 3 and other pollution in the flue gas After the material is discharged from the flue gas outlet 15. The slurry sprayed by the first slurry spray layer 3 and the second slurry spray layer 5 all come from the public slurry pool 7 at the lower part of the tower, contact with the flue gas and wash the pollutants in the flue gas, and then fall into the slurry pool 7, the slurry pool Containing a large amount of limestone and gypsum solution, the slurry tank 7 is equipped with a stirring device to prevent the precipitation of limestone and gypsum; SO2 is dissolved in water after being absorbed by the slurry to generate sulfurous acid, and air is filled into the slurry tank to oxidize the sulfurous acid into sulfuric acid, which is combined with the slurry Calcium carbonate reacts to form gypsum.

此烟气处理装置占地面积小,脱硫除尘效果好,烟气流通阻力小,建造、运行成本低。 The flue gas treatment device occupies a small area, has good desulfurization and dust removal effects, small flue gas circulation resistance, and low construction and operation costs.

Claims (6)

1. the flue gas device for deep cleaning for efficient desulfurizing and dust collecting, comprise absorption tower, establish slurry pool (7) in absorption tower and be positioned at the smoke absorption district above slurry pool (7), circulating slurry sprinkling device (2) is established at smoke inlet (1) place, it is characterized in that, with dividing plate (14), smoke absorption is separated into the first uptake zone and the second uptake zone being positioned at the first side, uptake zone, the flue gas reentrant pathway (4) being flowed to the second uptake zone by the first uptake zone is established between dividing plate (14) and slurry pool (7), the first slurries spraying layer (3) is established in first uptake zone, the second slurries spraying layer (5) is established in second uptake zone, first slurries spraying layer (3), second slurries spraying layer (5) is all connected with slurry pool (7) by slurry circulating pump (6) with circulating slurry sprinkling device (2), second slurries spraying layer (5) top establishes demister (8) from bottom to top successively, deduster (9) and exhanst gas outlet (15).
2. device as claimed in claim 1, it is characterized in that, also be provided with chilling spray protective device (13) at smoke inlet (1) place, chilling spray protective device (13) is connected with water source (10) by autocontrol valve (12); Between slurry circulating pump (6) and circulating slurry sprinkling device (2), establish flow detector (11), flow detector (11) is connected with autocontrol valve (12).
3. device as claimed in claim 1 or 2, is characterized in that, establish agitating device and oxidation air distribution device in described slurry pool (7).
4. device as claimed in claim 1 or 2, it is characterized in that, described deduster (9) is wet electrical dust precipitator.
5. device as claimed in claim 1 or 2, is characterized in that, the position of described exhanst gas outlet (15) is higher than the position of described smoke inlet (1).
6. device as claimed in claim 1 or 2, is characterized in that, the inwall on described absorption tower establishes line with rubber or lining glass flake anticorrosive coat.
CN201520156073.XU 2015-03-19 2015-03-19 A kind of flue gas device for deep cleaning for efficient desulfurizing and dust collecting Expired - Lifetime CN204502785U (en)

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Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN104722194A (en) * 2015-03-19 2015-06-24 永清环保股份有限公司 Deep flue gas purification device for efficient desulphurization and dust removal
CN105233604A (en) * 2015-10-20 2016-01-13 西安墙体材料研究设计院 Purification device for conducting flue gas desulfurization and dedusting on brick and tile kiln
CN113521944A (en) * 2021-07-06 2021-10-22 中钢集团天澄环保科技股份有限公司 System and method for dust removal and iron powder recovery of iron-containing dust in gas-based ironmaking production line

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN104722194A (en) * 2015-03-19 2015-06-24 永清环保股份有限公司 Deep flue gas purification device for efficient desulphurization and dust removal
CN105233604A (en) * 2015-10-20 2016-01-13 西安墙体材料研究设计院 Purification device for conducting flue gas desulfurization and dedusting on brick and tile kiln
CN113521944A (en) * 2021-07-06 2021-10-22 中钢集团天澄环保科技股份有限公司 System and method for dust removal and iron powder recovery of iron-containing dust in gas-based ironmaking production line

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