CN202387342U - Wet-type electric dedusting device - Google Patents
Wet-type electric dedusting device Download PDFInfo
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- CN202387342U CN202387342U CN2011204702880U CN201120470288U CN202387342U CN 202387342 U CN202387342 U CN 202387342U CN 2011204702880 U CN2011204702880 U CN 2011204702880U CN 201120470288 U CN201120470288 U CN 201120470288U CN 202387342 U CN202387342 U CN 202387342U
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- 239000007788 liquid Substances 0.000 claims abstract description 57
- 239000000779 smoke Substances 0.000 claims abstract description 55
- UGFAIRIUMAVXCW-UHFFFAOYSA-N Carbon monoxide Chemical compound [O+]#[C-] UGFAIRIUMAVXCW-UHFFFAOYSA-N 0.000 claims abstract description 30
- 239000003546 flue gas Substances 0.000 claims abstract description 30
- 238000010521 absorption reaction Methods 0.000 claims abstract description 20
- 239000000428 dust Substances 0.000 claims abstract description 17
- 239000007921 spray Substances 0.000 claims description 44
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims description 12
- 239000012716 precipitator Substances 0.000 claims description 7
- 238000007599 discharging Methods 0.000 claims 7
- 238000005507 spraying Methods 0.000 claims 1
- 239000012719 wet electrostatic precipitator Substances 0.000 abstract description 35
- 239000003344 environmental pollutant Substances 0.000 abstract description 17
- 231100000719 pollutant Toxicity 0.000 abstract description 17
- 239000010419 fine particle Substances 0.000 abstract description 7
- 239000000443 aerosol Substances 0.000 abstract description 6
- 150000001875 compounds Chemical class 0.000 abstract description 6
- 238000003912 environmental pollution Methods 0.000 abstract description 4
- 238000011010 flushing procedure Methods 0.000 abstract description 4
- 239000003595 mist Substances 0.000 description 9
- 239000002253 acid Substances 0.000 description 8
- 239000000463 material Substances 0.000 description 7
- 238000005260 corrosion Methods 0.000 description 5
- 238000005516 engineering process Methods 0.000 description 5
- 230000007797 corrosion Effects 0.000 description 4
- 239000002131 composite material Substances 0.000 description 3
- 230000000694 effects Effects 0.000 description 3
- 230000007613 environmental effect Effects 0.000 description 3
- 229910001385 heavy metal Inorganic materials 0.000 description 3
- 239000007787 solid Substances 0.000 description 3
- 239000000126 substance Substances 0.000 description 3
- 239000004743 Polypropylene Substances 0.000 description 2
- 238000011161 development Methods 0.000 description 2
- 229910052602 gypsum Inorganic materials 0.000 description 2
- 239000010440 gypsum Substances 0.000 description 2
- QSHDDOUJBYECFT-UHFFFAOYSA-N mercury Chemical compound [Hg] QSHDDOUJBYECFT-UHFFFAOYSA-N 0.000 description 2
- 229910052753 mercury Inorganic materials 0.000 description 2
- 229920001155 polypropylene Polymers 0.000 description 2
- 229910001220 stainless steel Inorganic materials 0.000 description 2
- 239000010935 stainless steel Substances 0.000 description 2
- VEXZGXHMUGYJMC-UHFFFAOYSA-N Hydrochloric acid Chemical compound Cl VEXZGXHMUGYJMC-UHFFFAOYSA-N 0.000 description 1
- 239000000809 air pollutant Substances 0.000 description 1
- 231100001243 air pollutant Toxicity 0.000 description 1
- 239000003513 alkali Substances 0.000 description 1
- 230000009286 beneficial effect Effects 0.000 description 1
- 238000013461 design Methods 0.000 description 1
- 238000010586 diagram Methods 0.000 description 1
- 238000005367 electrostatic precipitation Methods 0.000 description 1
- 238000005265 energy consumption Methods 0.000 description 1
- 239000003365 glass fiber Substances 0.000 description 1
- 238000009434 installation Methods 0.000 description 1
- 239000008258 liquid foam Substances 0.000 description 1
- 230000007774 longterm Effects 0.000 description 1
- 238000012423 maintenance Methods 0.000 description 1
- 229910052751 metal Inorganic materials 0.000 description 1
- 239000002184 metal Substances 0.000 description 1
- 150000002739 metals Chemical class 0.000 description 1
- 238000000034 method Methods 0.000 description 1
- 238000012821 model calculation Methods 0.000 description 1
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- 238000004064 recycling Methods 0.000 description 1
- 238000004088 simulation Methods 0.000 description 1
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- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02A—TECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
- Y02A50/00—TECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE in human health protection, e.g. against extreme weather
- Y02A50/20—Air quality improvement or preservation, e.g. vehicle emission control or emission reduction by using catalytic converters
- Y02A50/2351—Atmospheric particulate matter [PM], e.g. carbon smoke microparticles, smog, aerosol particles, dust
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- Treating Waste Gases (AREA)
Abstract
本实用新型公开了一种湿式电除尘装置,包括湿式吸收塔、导烟管道、湿式电除尘器和排烟管道,在湿式吸收塔上设有烟气入口,导烟管道的前端连接在湿式吸收塔上端,导烟管道的后端连接在湿式电除尘器上端,排烟管道的前端连接在湿式电除尘器的下端,排烟管道的后端与烟囱连通,所述湿式电除尘器竖向设置,烟气从上向下经过湿式电除尘器进入排烟管道。本实用新型湿式电除尘器设置在导烟管道后端下方,使烟气向下流动,阳极板上的冲洗液顺流向下,方向与烟气流向一致,便于阳极板收集烟气中的微细颗粒物及气溶胶,实现了烟气中复合污染物的高效脱除,减少了环境污染,满足了不断提高的大气排放标准。
The utility model discloses a wet type electric dust removal device, which comprises a wet type absorption tower, a smoke guide pipe, a wet type electric dust collector and a smoke exhaust pipe, a smoke inlet is arranged on the wet type absorption tower, the front end of the smoke guide pipe is connected to At the upper end of the tower, the rear end of the smoke guide pipe is connected to the upper end of the wet electrostatic precipitator, the front end of the smoke exhaust pipe is connected to the lower end of the wet electrostatic precipitator, and the rear end of the smoke exhaust pipe is connected to the chimney. The wet electrostatic precipitator is installed vertically , the flue gas enters the exhaust pipe through the wet electrostatic precipitator from top to bottom. The wet electrostatic precipitator of the utility model is arranged under the rear end of the smoke guide pipe, so that the flue gas flows downward, and the flushing liquid on the anode plate flows downward, and the direction is consistent with the flow direction of the flue gas, which is convenient for the anode plate to collect fine particles in the flue gas And aerosol, realize the efficient removal of compound pollutants in flue gas, reduce environmental pollution, and meet the continuously improving air emission standards.
Description
技术领域 technical field
本实用新型涉及环保技术领域,特别是一种湿式电除尘装置。The utility model relates to the technical field of environmental protection, in particular to a wet electric dust removal device.
背景技术 Background technique
随着人们对微细粉尘、酸雾、重金属等复合污染物危害环境及身体健康的认识不断提高,促使大气污染物排放标准的不断提高,新的排放标准要求微细颗粒物、酸雾、重金属等污染物的排放水平更低,传统的烟气吸收装置对烟气中部分污染物有较好的控制效果,但微细粉尘、重金属、SO3酸雾等复合污染物仍是被重点关注且需急切解决的难题。With the continuous improvement of people's awareness of the harm to the environment and health of composite pollutants such as fine dust, acid mist, and heavy metals, the emission standards of air pollutants have been continuously improved. The new emission standards require pollutants such as fine particles, acid mist, and heavy metals The emission level is lower, and the traditional flue gas absorption device has a good control effect on some pollutants in the flue gas, but composite pollutants such as fine dust, heavy metals, and SO 3 acid mist are still the focus of attention and need to be resolved urgently problem.
烟气经过吸收塔洗涤后,未被吸收的微细粉尘、SO3酸雾等复合污染物不仅产生二次污染,更重要的是会对人们的健康产生严重的危害。烟囱风向的下游,经常可以见到所谓的“石膏雨”,或者是有长长烟尾的“蓝烟”。随着工业的不断发展,大气复合污染物对环境造成的危害越来越严重,现有的去除烟气中复合污染物的技术仍不能达到理想的效果,因此十分有必要探究一种新的、高效去除微细粉尘、SO3酸雾等复合污染物的技术来减少环境污染。After the flue gas is washed by the absorption tower, the unabsorbed fine dust, SO 3 acid mist and other compound pollutants not only cause secondary pollution, but more importantly, cause serious harm to people's health. Downstream of the chimney wind direction, the so-called "gypsum rain" or "blue smoke" with long tails can often be seen. With the continuous development of industry, the harm caused by atmospheric compound pollutants to the environment is becoming more and more serious. The existing technology for removing compound pollutants in flue gas still cannot achieve the desired effect. Therefore, it is very necessary to explore a new, Efficient removal of complex pollutants such as fine dust, SO 3 acid mist and other technologies to reduce environmental pollution.
作为大气复合污染物的终端精细处理设备,湿式电除尘器可用于控制酸雾、微细粉尘、汞、金属等物质的排放。早在1907年,湿式电除尘器(WESP)技术就已经被应用去除酸雾羽烟,随着技术的不断发展,WESP不断被推广到多个工业领域。在燃煤电厂应用的测试中表明,WESP能去除90%以上的微细粉尘、SO3烟雾,并能达到近乎零浊度排放,此外WESP技术还能用于去除汞,吸收部分SO2和HCl。WESP作为烟气终端精细处理设备因具有压降小、操作简单、能耗小、无运动部件、维护费用低、除尘性能及可靠性高的特点越来越受到人们的关注。As a terminal fine treatment equipment for atmospheric composite pollutants, wet electrostatic precipitators can be used to control the discharge of acid mist, fine dust, mercury, metals and other substances. As early as 1907, wet electrostatic precipitator (WESP) technology has been applied to remove acid mist plume. With the continuous development of technology, WESP has been continuously extended to many industrial fields. Tests in coal-fired power plants have shown that WESP can remove more than 90% of fine dust and SO 3 smoke, and can achieve near-zero turbidity emissions. In addition, WESP technology can also be used to remove mercury and absorb part of SO 2 and HCl. As a flue gas terminal fine treatment equipment, WESP has attracted more and more attention because of its characteristics of small pressure drop, simple operation, low energy consumption, no moving parts, low maintenance cost, high dust removal performance and reliability.
实用新型内容Utility model content
本实用新型所要解决的问题就是提供一种湿式电除尘装置,结构简单,使用方便,同时高效脱除微细颗粒物及SO3等形成的气溶胶,减轻设备堵塞、烟囱腐蚀,可解决“烟囱雨”、“石膏雨”、“蓝烟”等技术难题,达到环保要求。The problem to be solved by the utility model is to provide a wet electrostatic precipitator, which has a simple structure and is easy to use, and at the same time efficiently removes aerosols formed by fine particles and SO 3 , etc., reduces equipment blockage and chimney corrosion, and can solve "chimney rain" , "gypsum rain", "blue smoke" and other technical problems, to meet environmental protection requirements.
为了解决上述技术问题,本实用新型采用如下技术方案:一种湿式电除尘装置,其特征在于:包括湿式吸收塔、导烟管道、湿式电除尘器和排烟管道,在湿式吸收塔上设有烟气入口,导烟管道的前端连接在湿式吸收塔上端,导烟管道的后端连接在湿式电除尘器上端,排烟管道的前端连接在湿式电除尘器的下端,排烟管道的后端与烟囱连通,所述湿式电除尘器竖向设置,烟气从上向下经过湿式电除尘器进入排烟管道。In order to solve the above technical problems, the utility model adopts the following technical solutions: a wet electrostatic precipitator, characterized in that it includes a wet absorption tower, a smoke guide pipe, a wet electrostatic precipitator and a smoke exhaust pipe, and the wet absorption tower is equipped with The flue gas inlet, the front end of the smoke guide pipe is connected to the upper end of the wet absorption tower, the rear end of the smoke guide pipe is connected to the upper end of the wet electrostatic precipitator, the front end of the smoke exhaust pipe is connected to the lower end of the wet electrostatic precipitator, and the rear end of the smoke exhaust pipe is Connected with the chimney, the wet electrostatic precipitator is installed vertically, and the flue gas enters the exhaust pipe through the wet electrostatic precipitator from top to bottom.
进一步的,所述湿式吸收塔包括塔体和平向设在塔体内上部的第一喷淋器,塔体上端与导烟管道的前端连接,塔体下部设有喷淋液池,所述烟气入口设在塔体上位于第一喷淋器和喷淋液池之间的位置,在塔体外侧设有循环泵,循环泵通过连接管分别与喷淋液池、第一喷淋器连接从而将喷淋液从喷淋液池输送至第一喷淋器。实现喷淋液的循环使用,节约资源。Further, the wet absorption tower includes a tower body and a first sprayer arranged in the upper part of the tower body in a horizontal direction, the upper end of the tower body is connected to the front end of the smoke guide pipe, and a spray liquid pool is provided at the lower part of the tower body, and the flue gas The inlet is located on the tower body between the first sprayer and the spray liquid tank, and a circulation pump is provided outside the tower body, and the circulation pump is respectively connected to the spray liquid pool and the first sprayer through connecting pipes so as to The spray liquid is delivered from the spray liquid tank to the first shower. Realize the recycling of spray liquid and save resources.
进一步的,所述塔体外侧设有风机,风机上接有送风管的一端,送风管伸入喷淋液池,送风管的另一端定位在连接管与喷淋液池的连接处。通过送风管把空气送入到喷淋液池内,对喷淋液进行氧化。Further, a fan is provided on the outside of the tower, and one end of the air supply pipe is connected to the fan, and the air supply pipe extends into the spray liquid pool, and the other end of the air supply pipe is positioned at the joint between the connecting pipe and the spray liquid pool . The air is sent into the spray liquid pool through the air supply pipe to oxidize the spray liquid.
进一步的,所述喷淋液池中设有搅拌器。使鼓入的空气在喷淋液中的均匀分布及防止含固物料的沉降。Further, a stirrer is provided in the spray liquid pool. Make the blown air evenly distributed in the spray liquid and prevent the settlement of solid-containing materials.
进一步的,所述导烟管道中设有导流板。使烟气均匀流入湿式电除尘器。Further, a deflector is provided in the smoke guiding duct. Make the flue gas evenly flow into the wet electrostatic precipitator.
进一步的,所述湿式电除尘器包括壳体、第二喷淋器、至少两块阳极板和至少一组阴极框架,壳体上端与导烟管道的后端连接,阳极板竖向平行固定在壳体中,两两阳极板之间竖向设置至少一组阴极框架,阴极框架中设有多根阴极线,阴极线通过导线与外部电源电连接,第二喷淋器平向固定在壳体上部且位于阳极板和阴极框架上方,壳体外部设有水泵并通过第一水管与第二喷淋器连接。Further, the wet electrostatic precipitator includes a housing, a second shower, at least two anode plates and at least one set of cathode frames, the upper end of the housing is connected to the rear end of the smoke guide pipe, and the anode plates are vertically fixed in parallel on the In the casing, at least one set of cathode frames are vertically arranged between two anode plates, and a plurality of cathode wires are arranged in the cathode frames, and the cathode wires are electrically connected to the external power supply through wires, and the second shower is fixed on the casing horizontally The upper part is located above the anode plate and the cathode frame, and a water pump is arranged outside the casing and connected to the second shower through the first water pipe.
进一步的,所述壳体上端设有阳极板挂架和阴极挂架,阳极板挂架位于阴极挂架上方,阳极板上端固定在阳极板挂架上,阴极框架上端固定在阴极挂架上,壳体下端设有阳极板支撑架,阳极板下端固定在阳极板支撑架上,两两相近的阳极板之间的距离为300~450mm。Further, the upper end of the housing is provided with an anode plate hanger and a cathode hanger, the anode plate hanger is located above the cathode hanger, the upper end of the anode plate is fixed on the anode plate hanger, and the upper end of the cathode frame is fixed on the cathode hanger, The lower end of the casing is provided with an anode plate support frame, and the lower end of the anode plate is fixed on the anode plate support frame, and the distance between two adjacent anode plates is 300-450 mm.
进一步的,所述排烟管道的前半段为U形段,U形段的前端与壳体的下端连接,U形段的后端与排烟管道的后半段连接,U形段的前端内部平向设有至少一层多孔分布板,多孔分布板的开孔率大于30%,U形段的下部设有集液器,集液器上接有导流管连接到喷淋液池中。设置U形段,便于集液器收集阳极板表面收集的污染物液体。Further, the first half of the smoke exhaust pipe is a U-shaped section, the front end of the U-shaped section is connected to the lower end of the housing, the rear end of the U-shaped section is connected to the second half of the smoke exhaust pipe, and the inside of the front end of the U-shaped section There is at least one layer of porous distribution plate in the horizontal direction, the opening ratio of the porous distribution plate is greater than 30%, and the lower part of the U-shaped section is provided with a liquid collector, and the liquid collector is connected with a guide pipe connected to the spray liquid pool. The U-shaped section is set to facilitate the liquid collector to collect the pollutant liquid collected on the surface of the anode plate.
进一步的,所述U形段中与集液器对应处设有百叶格栅,百叶格栅沿烟气流向向上倾斜设置且与烟气流向之间的夹角为30°~65°。减少液沫夹带,破碎气泡。Further, the U-shaped section is provided with a louver grill corresponding to the liquid collector, and the louver grill is arranged obliquely upward along the smoke flow direction and the angle between the louver grill and the smoke flow direction is 30°-65°. Reduce liquid entrainment and break up air bubbles.
进一步的,所述排烟管道的后半段为平向段,平向段的前端设有波纹除雾器,波纹除雾器的前方竖向设有第三喷淋器,第三喷淋器通过第二水管与水泵连接。平向段高于U形段,使阳极板表面收集的污染物液体不致流入波纹除雾器,保证第三喷淋器和波纹除雾器的长期正常使用。Further, the second half of the smoke exhaust pipe is a flat section, the front end of the flat section is provided with a corrugated demister, and a third sprayer is vertically provided in front of the corrugated demister, and the third sprayer passes through the first Two water pipes are connected with the water pump. The flat section is higher than the U-shaped section, so that the pollutant liquid collected on the surface of the anode plate will not flow into the corrugated demister, ensuring the long-term normal use of the third sprayer and the corrugated demister.
采用上述技术方案后,本实用新型具有如下优点:湿式电除尘器设置在导烟管道后端下方,使烟气向下流动,阳极板上的冲洗液顺流向下,方向与烟气流向一致,便于阳极板收集烟气中的微细颗粒物及气溶胶,实现了烟气中复合污染物的高效脱除,减少了环境污染,满足了不断提高的大气排放标准。After adopting the above technical scheme, the utility model has the following advantages: the wet electrostatic precipitator is arranged under the rear end of the smoke guide pipe, so that the flue gas flows downward, and the flushing liquid on the anode plate flows downward, and the direction is consistent with the flue gas flow direction. It is convenient for the anode plate to collect fine particles and aerosols in the flue gas, realize the efficient removal of compound pollutants in the flue gas, reduce environmental pollution, and meet the continuously improving air emission standards.
附图说明 Description of drawings
下面结合附图对本实用新型作进一步说明:Below in conjunction with accompanying drawing, the utility model is further described:
图1为本实用新型一种实施例的结构示意图。Fig. 1 is a schematic structural view of an embodiment of the utility model.
具体实施方式 Detailed ways
如图1所示本实用新型一种实施例的结构示意图,一种湿式电除尘装置,包括湿式吸收塔1、导烟管道2、湿式电除尘器3和排烟管道4,在湿式吸收塔上设有烟气入口10,导烟管道的前端连接在湿式吸收塔上端,导烟管道的后端连接在湿式电除尘器上端,排烟管道的前端连接在湿式电除尘器的下端,排烟管道的后端与烟囱9连通,所述湿式电除尘器竖向设置,烟气从上向下经过湿式电除尘器进入排烟管道。As shown in Figure 1, a structural schematic diagram of an embodiment of the utility model, a wet electrostatic precipitator, including a wet absorption tower 1, a smoke guide pipe 2, a wet
在上述实施例中,所述湿式吸收塔包括塔体11和平向设在塔体内上部的第一喷淋器12,塔体上端与导烟管道的前端连接,塔体下部设有喷淋液池13,所述烟气入口设在塔体上位于第一喷淋器和喷淋液池之间的位置,在塔体外侧设有循环泵14,循环泵通过连接管15分别与喷淋液池、第一喷淋器连接从而将喷淋液从喷淋液池输送至第一喷淋器。湿式吸收塔内通常不设置除雾器,必要时,也可设置1~2级平板式或屋脊式除雾器。在这里,导烟管道的前端也可以直接与塔体上端一体设置。In the above embodiment, the wet absorption tower includes a
在上述结构基础上,作进一步改进,塔体外侧设有风机16,风机上接有送风管17的一端,送风管伸入喷淋液池,送风管的另一端定位在连接管与喷淋液池的连接处。还可以在喷淋液池中设置搅拌器18。On the basis of the above structure, a further improvement is made. A
在上述实施例的结构基础上,导烟管道中设置导流板21,使烟气由导烟管道均匀进入到湿式电除尘器中,通过数值模拟和物理模型计算确定导流板的结构形式及安装位置,材料要求耐腐蚀和耐磨损。On the basis of the structure of the above-mentioned embodiments, a
在上述实施例中,所述湿式电除尘器包括壳体31、第二喷淋器32、至少两块阳极板33和至少一根阴极框架34,阳极板和阴极框架的数量根据湿式电除尘器的尺寸大小来决定,在本实施例中设置了五块阳极板和四根阴极框架。壳体上端与导烟管道的后端连接,阳极板竖向平行固定在壳体中,两两阳极板之间竖向设置一根阴极线,阴极线通过导线与外部电源35电连接,第二喷淋器平向固定在壳体上部且位于阳极板和阴极框架上方,壳体外部设有水泵5并通过第一水管36与第二喷淋器连接。具体来讲,壳体上端设有阳极板挂架37和阴极挂架38,阳极板挂架位于阴极挂架上方,阳极板上端固定在阳极板挂架上,阴极框架上端固定在阴极挂架上,壳体下端设有阳极板支撑架39,阳极板下端固定在阳极板支撑架上,两两相近的阳极板之间的距离为300~450mm,一般优选300mm、350mm、400mm或450mm。阳极板的高度可根据现场场地条件及设计需要确定,一般的高度变化范围在4~8m;阴极线优选了带针刺的方形管,具有较低的起晕电压并能产生强烈的电晕。第二喷淋器连续地喷向阳极板,阳极板上的冲洗液顺流向下,方向与烟气流向一致,在阳极板的正反表面形成均匀液膜,保持阳极板表面的可导电性,利于荷电的颗粒物向阳极表面移动,提高集尘效率。湿式电除尘器的内部环境条件恶劣,因此其内部结构的材料均应采用防腐材料,防止冲洗液对结构造成腐蚀,阳极板通常采用不锈钢或具有表面导电性能的玻璃纤维(FRP),阴极线应用不锈钢材料制作。在本实施例中,湿式电除尘器设置为单级,对微细颗粒物及气溶胶的脱除效率为90~99%,也可以设置二级、三级……设置二到三级湿式电除尘器对微细颗粒物及气溶胶脱除效率为99~99.99%,因此一般不会设置超过三级。In the above embodiment, the wet electrostatic precipitator includes a
所述排烟管道的前半段为U形段41,U形段的前端与壳体的下端连接,U形段的后端与排烟管道的后半段连接,U形段的前端内部平向设有至少一层多孔分布板42,多孔分布板的开孔率大于30%,要防止堵塞,需采用耐腐蚀的材料,能够保证湿式电除尘器内气流流场的稳定;U形段的下部设有集液器43,集液器上接有导流管44连接到喷淋液池中。阳极板表面收集的污染物液体中含有难溶的固体物质,容易沉积堵塞,且具有很强的酸、碱腐蚀性,集液器是把阳极板收集并冲洗下来含难溶固体物质的污染物液体收集自流回到湿式吸收塔的喷淋液池中,并形成液封,导流管宜有一定向下倾斜的坡度,便于污染物液体流入喷淋液池,不易堵塞。The first half of the smoke exhaust pipe is a
此外在U形段中与集液器对应处设有百叶格栅45,百叶格栅沿烟气流向向上倾斜设置且与烟气流向之间的夹角为30~65°,优选30°、45°或者60°。具体来说,百叶格栅设置在U形段中相对水平的位置,可减少液沫夹带和破碎气泡的作用,应采用耐腐蚀性能的材料,通常为聚丙烯(PP)、聚氯乙烯(PVC)、FRP等。排烟管道的后半段为平向段46,平向段的前端设有波纹除雾器47,波纹除雾器的前方竖向设有第三喷淋器48,第三喷淋器通过第二水管49与水泵连接。波纹除雾器由第三喷淋器间断冲洗清洁表面,保证除雾器表面干净,内部不堵塞。In addition, a
上述实施例中,烟气经烟气入口进入湿式吸收塔,通过循环泵将喷淋液输送至第一喷淋器,经第一喷淋器雾化后对烟气中的目标组分进行洗涤吸收,洗涤后的低温烟气通过导烟管道均匀进入到湿式电除尘器,经过电除尘后去除烟气中的微细颗粒物及气溶胶,最后经排烟管道除雾后得到净化,通过烟囱9排入大气。本实用新型实现了烟气中复合污染物的高效脱除,减少了环境污染,满足了不断提高的大气排放标准。In the above embodiment, the flue gas enters the wet absorption tower through the flue gas inlet, and the spray liquid is transported to the first sprayer through the circulation pump, and the target components in the flue gas are washed after being atomized by the first sprayer Absorption, the washed low-temperature flue gas enters the wet electrostatic precipitator evenly through the smoke guide pipe, removes fine particles and aerosols in the flue gas after electrostatic precipitation, and finally gets purified after demisting through the smoke exhaust pipe, and passes through the chimney 9 into the atmosphere. The utility model realizes the high-efficiency removal of compound pollutants in the smoke, reduces environmental pollution, and satisfies the continuously increasing air emission standards.
除上述优选实施例外,本实用新型还有其他的实施方式,本领域技术人员可以根据本实用新型作出各种改变和变形,只要不脱离本实用新型的精神,均应属于本实用新型所附权利要求所定义的范围。In addition to the above-mentioned preferred embodiment, the utility model also has other implementation modes, those skilled in the art can make various changes and deformations according to the utility model, as long as they do not depart from the spirit of the utility model, all should belong to the appended rights of the utility model The scope defined by the requirement.
Claims (10)
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Cited By (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN102500188A (en) * | 2011-11-23 | 2012-06-20 | 浙江菲达脱硫工程有限公司 | Wet type electric dust-removing device |
| CN108404663A (en) * | 2018-06-01 | 2018-08-17 | 福建龙净脱硫脱硝工程有限公司 | A kind of integrated form smoke eliminator |
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Cited By (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN102500188A (en) * | 2011-11-23 | 2012-06-20 | 浙江菲达脱硫工程有限公司 | Wet type electric dust-removing device |
| CN108404663A (en) * | 2018-06-01 | 2018-08-17 | 福建龙净脱硫脱硝工程有限公司 | A kind of integrated form smoke eliminator |
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