CN203777877U - Electrostatic composite fume dedusting and demisting device - Google Patents
Electrostatic composite fume dedusting and demisting device Download PDFInfo
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- CN203777877U CN203777877U CN201420153725.XU CN201420153725U CN203777877U CN 203777877 U CN203777877 U CN 203777877U CN 201420153725 U CN201420153725 U CN 201420153725U CN 203777877 U CN203777877 U CN 203777877U
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- 239000002131 composite material Substances 0.000 title claims abstract description 26
- 239000003517 fume Substances 0.000 title 1
- 239000000428 dust Substances 0.000 claims abstract description 123
- 239000003546 flue gas Substances 0.000 claims abstract description 80
- UGFAIRIUMAVXCW-UHFFFAOYSA-N Carbon monoxide Chemical compound [O+]#[C-] UGFAIRIUMAVXCW-UHFFFAOYSA-N 0.000 claims abstract description 77
- 239000003595 mist Substances 0.000 claims abstract description 64
- 239000000779 smoke Substances 0.000 claims abstract description 18
- 230000005684 electric field Effects 0.000 claims abstract description 7
- 239000010935 stainless steel Substances 0.000 claims description 7
- 229910001220 stainless steel Inorganic materials 0.000 claims description 7
- 239000010865 sewage Substances 0.000 claims description 5
- 239000010813 municipal solid waste Substances 0.000 claims description 4
- 229910000851 Alloy steel Inorganic materials 0.000 claims description 3
- 238000006477 desulfuration reaction Methods 0.000 abstract description 23
- 230000023556 desulfurization Effects 0.000 abstract description 22
- 239000010440 gypsum Substances 0.000 abstract description 13
- 229910052602 gypsum Inorganic materials 0.000 abstract description 13
- 238000010521 absorption reaction Methods 0.000 abstract description 12
- 238000000746 purification Methods 0.000 abstract description 9
- 230000000694 effects Effects 0.000 abstract description 3
- 101000623895 Bos taurus Mucin-15 Proteins 0.000 abstract 1
- 239000000203 mixture Substances 0.000 abstract 1
- 239000002002 slurry Substances 0.000 description 12
- 239000007788 liquid Substances 0.000 description 11
- 239000002245 particle Substances 0.000 description 10
- 238000000034 method Methods 0.000 description 6
- 239000004744 fabric Substances 0.000 description 4
- 239000012719 wet electrostatic precipitator Substances 0.000 description 4
- 239000003245 coal Substances 0.000 description 3
- 238000010586 diagram Methods 0.000 description 3
- 239000000835 fiber Substances 0.000 description 3
- 229910052736 halogen Inorganic materials 0.000 description 3
- 150000002367 halogens Chemical class 0.000 description 3
- 235000019738 Limestone Nutrition 0.000 description 2
- 230000009286 beneficial effect Effects 0.000 description 2
- OSGAYBCDTDRGGQ-UHFFFAOYSA-L calcium sulfate Chemical compound [Ca+2].[O-]S([O-])(=O)=O OSGAYBCDTDRGGQ-UHFFFAOYSA-L 0.000 description 2
- 239000011152 fibreglass Substances 0.000 description 2
- 239000006028 limestone Substances 0.000 description 2
- 230000000630 rising effect Effects 0.000 description 2
- 238000003723 Smelting Methods 0.000 description 1
- 230000002745 absorbent Effects 0.000 description 1
- 239000002250 absorbent Substances 0.000 description 1
- 239000000809 air pollutant Substances 0.000 description 1
- 231100001243 air pollutant Toxicity 0.000 description 1
- 230000000712 assembly Effects 0.000 description 1
- 238000000429 assembly Methods 0.000 description 1
- 238000000889 atomisation Methods 0.000 description 1
- 238000006243 chemical reaction Methods 0.000 description 1
- 230000015271 coagulation Effects 0.000 description 1
- 238000005345 coagulation Methods 0.000 description 1
- 238000002485 combustion reaction Methods 0.000 description 1
- 238000013329 compounding Methods 0.000 description 1
- 150000001875 compounds Chemical class 0.000 description 1
- 239000004020 conductor Substances 0.000 description 1
- 238000005260 corrosion Methods 0.000 description 1
- TXKMVPPZCYKFAC-UHFFFAOYSA-N disulfur monoxide Inorganic materials O=S=S TXKMVPPZCYKFAC-UHFFFAOYSA-N 0.000 description 1
- 230000005611 electricity Effects 0.000 description 1
- 239000012717 electrostatic precipitator Substances 0.000 description 1
- 230000003203 everyday effect Effects 0.000 description 1
- 239000013305 flexible fiber Substances 0.000 description 1
- -1 flue gas compound Chemical class 0.000 description 1
- 238000011010 flushing procedure Methods 0.000 description 1
- 230000005484 gravity Effects 0.000 description 1
- 238000009434 installation Methods 0.000 description 1
- 239000000463 material Substances 0.000 description 1
- 229910052751 metal Inorganic materials 0.000 description 1
- 239000002184 metal Substances 0.000 description 1
- 238000010248 power generation Methods 0.000 description 1
- 239000012716 precipitator Substances 0.000 description 1
- 239000007921 spray Substances 0.000 description 1
- 238000005507 spraying Methods 0.000 description 1
- 230000003068 static effect Effects 0.000 description 1
- XTQHKBHJIVJGKJ-UHFFFAOYSA-N sulfur monoxide Chemical compound S=O XTQHKBHJIVJGKJ-UHFFFAOYSA-N 0.000 description 1
- 230000009466 transformation Effects 0.000 description 1
- 239000002918 waste heat Substances 0.000 description 1
- 239000002699 waste material Substances 0.000 description 1
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Abstract
本实用新型涉及一种用于湿法脱硫尾端烟气深度净化处理的烟气静电复合除尘除雾装置,箱体内按烟气流向依次设有静电聚尘组件I、惯性除尘除雾组件II和静电除尘除雾组件Ⅲ;静电聚尘组件I由互相平行且间距排列的多个聚尘阳极板及设置在相邻两聚尘阳极板间的一对阴极线组成,该阴极线与聚尘阳极板之间形成电场;惯性除尘除雾组件II由互相平行且间距排列的多个收集板组成;静电除尘除雾组件Ⅲ由互相平行且间距排列的多个除尘除雾阳极板和多个阴极线组成,二者之间形成电场。本装置连接于脱硫吸收塔出口烟道上,实现对烟气深度除尘除雾的效果,解决了“石膏雨”、“大白烟”等污染现象,使烟尘达标排放。
The utility model relates to a flue gas electrostatic composite dedusting and mist removal device for the deep purification treatment of flue gas at the end of wet desulfurization. The box body is sequentially provided with an electrostatic dust collection component I, an inertial dust removal and mist removal component II and Electrostatic dust removal and mist removal assembly III; electrostatic dust collection assembly I is composed of a plurality of dust-collecting anode plates arranged in parallel and at intervals and a pair of cathode wires arranged between two adjacent dust-collection anode plates. An electric field is formed between the plates; the inertial dust and mist removal assembly II is composed of a plurality of collecting plates parallel to each other and arranged at intervals; the electrostatic dust and mist removal assembly III is composed of a plurality of dust removal and mist removal anode plates and a plurality of cathode lines arranged in parallel and at intervals Composition, an electric field is formed between the two. This device is connected to the outlet flue of the desulfurization absorption tower to achieve the effect of deep dust and fog removal on the flue gas, solve the pollution phenomena such as "gypsum rain" and "big white smoke", and make the smoke and dust discharge up to the standard.
Description
技术领域 technical field
本实用新型涉及一种除尘除雾设备,特别涉及针对燃煤发电厂湿法脱硫尾端烟气进行深度净化处理的烟气静电复合除尘除雾装置。 The utility model relates to a dust removal and mist removal device, in particular to a flue gas electrostatic composite dust removal and mist removal device for deep purification treatment of the flue gas at the tail end of wet desulfurization in a coal-fired power plant. the
背景技术 Background technique
某些以燃煤为能源的行业,如火力发电、金属冶炼等大型企业每天需要消耗大量燃煤,煤燃烧产生的大量粉尘随烟气排放,由于烟尘对环境危害极大,因此国内对烟尘排放浓度有严格的限制。例如,国家标准(火电厂大气污染物排放标准 GB 13223-2011)明确规定烟尘排放浓度限值为30 mg/Nm3,重点地区的排放浓度限值为20 mg/Nm3。为达到烟尘排放标准,燃煤系统必须设置烟气除尘设备。目前,烟气除尘设备主要为静电除尘器、袋式除尘器、电袋复合除尘器等种类。 Some industries that use coal as energy, such as thermal power generation, metal smelting and other large enterprises need to consume a large amount of coal every day, and a large amount of dust generated by coal combustion is discharged along with the flue gas. Concentrations are strictly limited. For example, the national standard (GB 13223-2011 Emission Standard of Air Pollutants for Thermal Power Plants) clearly stipulates that the emission concentration limit of smoke and dust is 30 mg/Nm 3 , and the emission concentration limit in key areas is 20 mg/Nm 3 . In order to meet the smoke and dust emission standards, the coal-fired system must be equipped with smoke and dust removal equipment. At present, the flue gas dedusting equipment mainly includes electrostatic precipitator, bag filter, electric bag composite precipitator and other types.
通常,火力发电厂的大型燃煤锅炉烟气的净化处理除除尘外,其必须还通过吸收塔进行脱硫反应,且近年来大部分火力发电厂已基本完成SCR脱硝改造。烟气经脱硝、除尘、脱硫净化后排放。通常,排放烟气多设有回收余热的空气预热器,在空预器或SCR脱硝反应器之后,脱硫吸收塔(下简称吸收塔)之前设置除尘器,使烟气含尘量降至<30 mg/Nm3。 Usually, in addition to dust removal, the flue gas purification treatment of large coal-fired boilers in thermal power plants must also undergo desulfurization reactions through absorption towers. In recent years, most thermal power plants have basically completed SCR denitrification transformation. The flue gas is discharged after denitrification, dust removal and desulfurization purification. Usually, the exhaust flue gas is equipped with an air preheater for recovering waste heat. After the air preheater or SCR denitrification reactor, a dust collector is installed before the desulfurization absorption tower (hereinafter referred to as the absorption tower) to reduce the dust content of the flue gas to < 30 mg/Nm 3 .
然而,烟气的湿法脱硫过程是以石灰石浆液为吸收剂,吸收塔内,石灰石浆液以喷淋雾化的方式与烟气接触而与烟气中的氧化硫反应,生成硫酸钙(石膏)等物质,其间,上升烟气与下降的雾状浆液之间发生极大的传质传热过程,烟气在吸收塔内上升过程中会挟带部分细小的石膏浆液(逃逸的石膏浆液),这些随烟气逃逸的石膏浆液会形成新的粉尘,导致烟气的粉尘浓度再次增高,虽然一般在吸收塔顶部设有机械除雾器,但机械除雾器的除雾能力小,除雾器通道易被石膏浆液堵塞,难以除净烟气夹带的石膏浆液,相当部分的石膏浆液随烟气排放,导致“石膏雨”、“大白烟”等污染现象时有发生。因此,即使烟气在脱硫前已将含尘量降至<30 mg/Nm3,但由于上述原因,脱硫后的烟气仍难以实现粉尘达标排放。为弥补此现象,专利文献CN 101460251 A,CN 102500188 A,CN103055644 A,CN 202538927 U等报导了在脱硫吸收塔出口增设湿式静电除尘器,用于对烟气进一步深度净化。然而,湿式静电除尘器占地面积大,系统复杂,投资高,很多火电厂场地条件无法满足增设湿式静电除尘器的要求。而且在进入脱硫吸收塔之前,烟气已经过了除尘处理,烟尘已经接近达标浓度,仅为了脱除浆液挟带而新增的少量烟尘,投入巨资新建整套大型湿式静电除尘系统,其经济性很低,投资浪费严重。 However, the wet desulfurization process of flue gas uses limestone slurry as the absorbent. In the absorption tower, the limestone slurry contacts the flue gas in the form of spray atomization and reacts with the sulfur oxide in the flue gas to form calcium sulfate (gypsum) During the period, a huge mass and heat transfer process occurs between the rising flue gas and the falling mist slurry, and the flue gas will carry some fine gypsum slurry (escaping gypsum slurry) during the rising process in the absorption tower, The gypsum slurry that escapes with the flue gas will form new dust, which will cause the dust concentration of the flue gas to increase again. Although a mechanical demister is generally installed on the top of the absorption tower, the demisting ability of the mechanical demister is small, and the demister The channel is easily blocked by gypsum slurry, and it is difficult to remove the gypsum slurry entrained by the flue gas. A considerable part of the gypsum slurry is discharged with the flue gas, causing pollution phenomena such as "gypsum rain" and "big white smoke" to occur from time to time. Therefore, even if the dust content of the flue gas has been reduced to <30 mg/Nm 3 before desulfurization, due to the above reasons, it is still difficult for the flue gas after desulfurization to meet the dust discharge standard. To make up for this phenomenon, patent documents CN 101460251 A, CN 102500188 A, CN 103055644 A, CN 202538927 U, etc. report adding a wet electrostatic precipitator at the outlet of the desulfurization absorption tower for further deep purification of the flue gas. However, the wet electrostatic precipitator occupies a large area, the system is complex, and the investment is high. The site conditions of many thermal power plants cannot meet the requirements for adding a wet electrostatic precipitator. Moreover, before entering the desulfurization absorption tower, the flue gas has undergone dust removal treatment, and the dust concentration is close to the standard. It is only to remove a small amount of smoke and dust carried by the slurry, and invest a huge amount of money to build a large-scale wet electrostatic precipitator system. Its economical Very low, serious waste of investment.
发明内容 Contents of the invention
本实用新型目的是提供一种可安装在脱硫吸收塔出口烟道上的烟气复合除尘除雾装置,用于对排放前的脱硫烟气进一步深度净化,除净烟气中少量的残余粉尘及随雾沫带出的新增石膏粉尘,确保烟尘的达标排放。 The purpose of the utility model is to provide a flue gas compound dust and mist removal device that can be installed on the outlet flue of the desulfurization absorption tower, which is used for further deep purification of the desulfurization flue gas before discharge, and removes a small amount of residual dust in the flue gas. The newly added gypsum dust brought out by the mist ensures the discharge of smoke and dust up to the standard. the
本实用新型烟气复合除尘除雾装置包括箱体,箱体设有烟气进口和出口,箱体的底端设有出污口;所述箱体内按烟气流向依次设有静电聚尘组件(Ⅰ)、惯性除尘除雾组件(Ⅱ)和静电除尘除雾组件(Ⅲ);所述静电聚尘组件(Ⅰ)由互相平行且间距排列的多个聚尘阳极板及设置在相邻两聚尘阳极板间的一对阴极线组成,该阴极线与聚尘阳极板之间形成电场;所述惯性除尘除雾组件(Ⅱ)由互相平行且间距排列的多个收集板组成;所述静电除尘除雾组件(Ⅲ)由互相平行且间距排列的多个除尘除雾阳极板和间距排列的多个阴极线组成,该阴极线与除尘除雾阳极板之间形成电场;所述静电聚尘组件(Ⅰ)中的各相邻聚尘阳极板之间、所述惯性除尘除雾组件(Ⅱ)中的各相邻收集板之间以及所述静电除尘除雾组件(Ⅲ)中的各相邻除尘除雾阳极板之间均形成烟气通道。 The flue gas composite dedusting and mist removal device of the utility model includes a box body, the box body is provided with a flue gas inlet and an outlet, and the bottom end of the box body is provided with a sewage outlet; the box body is sequentially provided with electrostatic dust collection components according to the flow direction of the flue gas (I) , inertial dust removal and mist removal assembly (II) and electrostatic dust removal and mist removal assembly (Ⅲ); the electrostatic dust collection assembly (I) consists of a plurality of dust collection anode plates arranged in parallel Composed of a pair of cathode wires between the dust-collecting anode plates, an electric field is formed between the cathode wires and the dust-collecting anode plates; the inertial dust and mist removal assembly (II) is composed of a plurality of collecting plates that are parallel to each other and arranged at intervals; the The electrostatic dedusting and demisting assembly (Ⅲ) is composed of a plurality of anode plates for dedusting and demisting arranged in parallel and at intervals and a plurality of cathode lines arranged at intervals, and an electric field is formed between the cathode lines and the anode plates for dedusting and demisting; Between the adjacent dust-collecting anode plates in the dust assembly (I), between the adjacent collection plates in the inertial dust removal and mist removal assembly (II), and between each of the electrostatic dust removal and mist removal assemblies (III) Flue gas channels are formed between adjacent dust and mist removal anode plates.
所述惯性除尘除雾组件(Ⅱ)中的各收集板是形成连续曲面的“入”字形整体板,“入”字形整体板的顶端向上伸出段形成迎着烟气前进方向的弯耳。 Each collecting plate in the inertial dust and mist removal assembly (II) is an integral plate in the shape of an "in" shape with a continuous curved surface, and the top end of the integral plate in the shape of "in" protrudes upwards to form a curved ear facing the advancing direction of the smoke. the
所述惯性除尘除雾组件(Ⅱ)中的各收集板表面设有一个或多个拦污堰。 One or more trash weirs are arranged on the surface of each collecting plate in the inertial dust and mist removal assembly (II). the
各收集板的两端分别通过撑杆固定在箱体的壁面上。 The two ends of each collecting plate are respectively fixed on the wall surface of the box body through struts. the
所述静电聚尘组件(Ⅰ)和静电除尘除雾组件(Ⅲ)中的阴极线均为芒刺状导线。 The cathode wires in the electrostatic dust collection assembly (I) and the electrostatic dust removal and mist removal assembly (III) are all barbed wires. the
所述静电除尘除雾组件(Ⅲ)中的各除尘除雾阳极板是由一对平面板连接成的“人”字形组合板,每对平面板的顶端边连接在同一根顶端撑杆上,左、右两底端边分别连接在各自的底端撑杆上,各顶端撑杆和各底端撑杆的前后两端均分别固定在箱体的前后壁面上。 Each dust and fog anode plate in the electrostatic dust and fog removal assembly (Ⅲ) is a "herringbone" composite plate formed by connecting a pair of flat plates, and the top edges of each pair of flat plates are connected to the same top support bar. The left and right bottom ends are respectively connected to respective bottom struts, and the front and rear ends of each top strut and each bottom strut are respectively fixed on the front and rear walls of the box body. the
各顶端撑杆和各底端撑杆均通过插槽与除尘除雾阳极板对应端插接相连。 Each top strut and each bottom strut are plugged and connected to the corresponding ends of the dust and mist removal anode plate through slots. the
所述箱体壁面从烟气进口以下向箱内方向倾斜面斜面,以利于收集所捕获液体。 The wall surface of the box is inclined from below the flue gas inlet to the inside of the box, so as to facilitate the collection of the captured liquid. the
所述各阴极线以不锈钢或合金钢为材质。 The cathode wires are made of stainless steel or alloy steel. the
本装置包含了多级复合的除尘除雾系统,其中,静电聚尘组件对烟气进行一次荷电,一部分小液滴和粉尘聚集为大颗粒,然后通过“入”字形曲面板接触碰撞而使含尘雾气凝聚成液滴,并顺曲面板下落至箱底。剩余的微细液滴和微小粉尘通过二次强荷电被静电除尘除雾组件除去。因此,本装置利用静电原理和惯性原理多级复合,协同除尘除雾,能分离除去颗粒型的大、小粉尘和浆液型雾状液滴,实现对烟气深度除尘除雾的效果,而且结构简单,可方便地连接于脱硫吸收塔出口烟道上,弥补了烟气湿法脱硫后新增含浆雾滴难以的问题,成功地解决了“石膏雨”、“大白烟”等污染现象,使烟尘达标排放。 This device includes a multi-stage compound dust removal and fog removal system, in which the electrostatic dust collection component charges the flue gas once, and a part of the small liquid droplets and dust gather into large particles, and then through the contact and collision of the "in" shaped curved plate The dust-laden mist condenses into liquid droplets and falls to the bottom of the box along the curved panel. The remaining fine liquid droplets and fine dust are removed by the electrostatic dust and mist removal components through secondary strong charging. Therefore, this device uses the principle of static electricity and inertial multi-stage compounding to cooperate with dust and fog removal, and can separate and remove large and small particle-type dust and slurry-type mist droplets to achieve the effect of deep dust and fog removal on flue gas, and the structure It is simple and can be easily connected to the outlet flue of the desulfurization absorption tower, which makes up for the difficulty of adding slurry-containing droplets after wet desulfurization of flue gas, and successfully solves the pollution phenomena such as "gypsum rain" and "big white smoke", making it Smoke and dust discharge up to standard. the
附图说明 Description of drawings
图1是烟气复合除尘除雾装置的结构示意图。 Figure 1 is a structural schematic diagram of a flue gas composite dust and mist removal device. the
图2是“入”字形曲面板的结构示意图。 Fig. 2 is a schematic diagram of the structure of a curved panel in the shape of "入". the
图3是静电除尘除雾组件中的除尘除雾阳极板结构示意图。 Fig. 3 is a schematic diagram of the structure of the anode plate for dust and mist removal in the electrostatic dust removal and mist removal assembly. the
图4表示本除尘除雾装置在湿法脱硫尾端烟气深度净化系统中的安装位置。 Figure 4 shows the installation position of this dust and mist removal device in the deep purification system of flue gas at the end of wet desulfurization. the
图中:Ⅰ—静电聚尘组件,Ⅱ—惯性除尘除雾组件,Ⅲ—静电除尘除雾组件,1—烟气进口,2—箱体,2-1—斜面,3、6—阴极线,4—聚尘阳极板,5—收集板,5-1—弯耳,5-2—拦污堰,7—除尘除雾阳极板, 8—烟气出口,9—排污口,10—顶端撑杆,11—底端撑杆,12—脱硫塔,13—旁路烟道,14—尾端烟气出口烟道、15、16、17、18—挡板门,19—烟卤。 In the figure: Ⅰ—electrostatic dust collection component, Ⅱ—inertial dust and fog removal component, Ⅲ—electrostatic dust and fog removal component, 1—flue gas inlet, 2—box, 2-1—slope, 3, 6—cathode line, 4—dust collecting anode plate, 5—collecting plate, 5-1—bend ear, 5-2—pollution weir, 7—dust and mist removal anode plate, 8—flue gas outlet, 9—drain outlet, 10—top support Rod, 11—bottom support rod, 12—desulfurization tower, 13—bypass flue, 14—tail flue gas outlet flue, 15, 16, 17, 18—baffle door, 19—smoke halogen. the
具体实施方式 Detailed ways
下面结合附说明本实用新型复合除尘除雾装置的实施例结构及工作原理。 The structure and working principle of the embodiment of the composite dust and mist removal device of the present invention will be described below in conjunction with the appendix.
实施例1Example 1
结合图4和图1说明复合除尘除雾装置的结构和工作原理。 Combining Figure 4 and Figure 1, the structure and working principle of the composite dust and mist removal device are described.
来自湿法脱硫吸收塔12的尾端烟气从烟气进口1进入箱体2,净化后的烟气从箱体2的烟气出口8排出,烟气中被分离出的污液从箱体底部的的排污口9排出。 The tail flue gas from the wet desulfurization absorption tower 12 enters the box body 2 from the flue gas inlet 1, the purified flue gas is discharged from the flue gas outlet 8 of the box body 2, and the dirty liquid separated from the flue gas is discharged from the box body The sewage outlet 9 at the bottom is discharged. the
箱体2内按烟气流向依次设有静电聚尘组件Ⅰ、惯性除尘除雾组件Ⅱ和静电除尘除雾组件Ⅲ;下面分别说明各组件的结构。 The box body 2 is provided with an electrostatic dust collection unit I , an inertial dust removal and mist removal unit II and an electrostatic dust removal and mist removal unit III in sequence according to the flue gas flow direction; the structures of each unit are described below.
静电聚尘组件Ⅰ由多个互相平行且间距排列的聚尘阳极板4及阴极线3组成,两个相邻的聚尘阳极板4之间均设有一对阴极线3,形成正、负电极间隔布置。聚尘阳极板4材质为不锈钢或导电玻璃钢等刚性导电材质,板间距为350~450 mm。单块聚尘阳极板4的宽度为500 mm,长度为3000~8000 mm;阴极线3之间的间距为300~600 mm,阴极线3为不锈钢或合金钢材质的芒刺状线(下同)。阴极线3与聚尘阳极板4之间形成电场,聚尘阳极板4之间形成烟气通道。烟气从聚尘阳极板4之间通过时被一次荷电,即液滴及烟尘在不同极性分别荷正电和负电,有利于小颗粒碰撞凝聚转变为大颗粒,利于集尘。 The electrostatic dust collection assembly I is composed of a plurality of dust-collecting anode plates 4 and cathode wires 3 arranged in parallel and at intervals. A pair of cathode wires 3 are arranged between two adjacent dust-collection anode plates 4 to form positive and negative electrodes. Interval arrangement. Dust-collecting anode plate 4 is made of rigid conductive materials such as stainless steel or conductive glass fiber reinforced plastic, and the plate spacing is 350-450 mm. The width of the single dust-collecting anode plate 4 is 500 mm, and the length is 3000-8000 mm; the distance between the cathode wires 3 is 300-600 mm, and the cathode wires 3 are prickly wires made of stainless steel or alloy steel (the same below ). An electric field is formed between the cathode wire 3 and the dust-collecting anode plate 4 , and a flue gas channel is formed between the dust-collecting anode plates 4 . When the flue gas passes between the dust-collecting anode plates 4, it is charged once, that is, the liquid droplets and the smoke are charged positively and negatively at different polarities, which is beneficial for small particles to collide and agglomerate into large particles, which is beneficial for dust collection. the
惯性除尘除雾组件Ⅱ由互相平行且间距排列的多个收集板5组成;如图2,各收集板5是带有连续曲面的“入”字形整体板,图中箭头表示烟气在收集板5间的流向。“入”字形整体板人顶端形成迎着烟气前进方向的弯耳5-1,右侧板面设有一条(或多条)拦污堰5-2。收集板5的材质为PP或FRPP,易于成型,和具有防腐性能,板间距为50~500 mm。 The inertial dust and mist removal assembly II is composed of a plurality of collecting plates 5 arranged parallel to each other at intervals; as shown in Figure 2, each collecting plate 5 is an integral plate with a continuous curved surface. 5 flow directions. The top of the overall board in the shape of "入" forms a curved ear 5-1 facing the advancing direction of the smoke, and one (or more) trash weirs 5-2 are provided on the right side of the board. The collecting plate 5 is made of PP or FRPP, which is easy to form and has anti-corrosion properties, and the plate spacing is 50-500 mm. the
经静电聚尘组件Ⅰ一次荷电凝聚处理后的烟气进入本组件后,大颗粒液滴烟尘与各收集板5的曲面发生碰撞,液滴在收集板5上进一步聚集而增大,受惯性作用,大颗粒液滴顺着收集板5下滑,最后下落至箱底,从排污口9排出。弯耳5-1和拦污堰5-2均可将烟气中的污物拦下,防止被烟气流二次挟带。各收集板5的两端分别通过撑杆固定在箱体的壁面上,图2中,左右两圆形端可与撑杆插接相连(插接方式与图3相同)。 After the flue gas after the primary charging and coagulation treatment of the electrostatic dust collection component I enters the component, the large particles of smoke and dust collide with the curved surfaces of the collecting plates 5, and the droplets are further gathered on the collecting plates 5 to increase in size. As a result, the large-particle droplets slide down the collecting plate 5, and finally fall to the bottom of the box, and are discharged from the sewage outlet 9. Both the bent ear 5-1 and the trash weir 5-2 can stop the dirt in the flue gas to prevent it from being entrained by the flue gas flow for the second time. The two ends of each collecting plate 5 are respectively fixed on the wall surface of the box body by struts. In Fig. 2, the left and right circular ends can be connected with the struts by plugging (the plugging method is the same as that in Fig. 3). the
如图1,静电除尘除雾组件Ⅲ由互相平行且间距排列的多个除尘除雾阳极板7和若干个阴极线6组成,除尘除雾阳极板7以导电玻璃钢或柔性纤维织物为材质,板间距为50~500 mm,板间角度为60~120 o。如图3,各除尘除雾阳极板7是由一对平面板连接成“人”字形的组合板,每对平面板的顶端与同一根顶端撑杆10插接相连,“人”字形组合板的左、右两底端分别与各自的底端撑杆11插接相连,各顶端撑杆10和各底端撑杆11的前后两端均分别固定在箱体2的前后壁面上,顶端撑杆10和底端撑杆11的结构可以相同或不同。 As shown in Figure 1, the electrostatic dust and fog removal assembly III is composed of a plurality of dust and fog removal anode plates 7 and several cathode wires 6 arranged in parallel and at intervals. The dust and fog removal anode plates 7 are made of conductive glass fiber reinforced plastic or flexible fiber fabric. The spacing is 50~500 mm, and the angle between plates is 60~ 120o . As shown in Figure 3, each dust and mist removal anode plate 7 is a "herringbone" composite board connected by a pair of flat boards, and the top of each pair of flat boards is plugged and connected with the same top support rod 10. The left and right bottom ends of the left and right bottoms are respectively connected to the respective bottom struts 11, and the front and rear ends of each top strut 10 and each bottom strut 11 are respectively fixed on the front and rear walls of the box body 2, and the top struts The structure of the rod 10 and the bottom strut 11 may be the same or different.
经惯性除尘除雾组件Ⅱ除去大部分液滴和大颗粒粉尘后的烟气,在本静电除尘除雾组件Ⅲ,烟气中微细液滴和颗粒物被二次强荷电。由于荷电效应,微细液滴和颗粒物被除尘除雾阳极板7吸附,使其不被气流挟带,微细液滴和颗粒物在阳极板表面聚集后靠重力作用顺阳极板表面向下汇入箱体2底部,由排污口9排出。经净化的烟气从烟气出口8达标排放,完成脱硫烟气的深度除尘除雾。 The flue gas after most of the liquid droplets and large particles of dust are removed by the inertial dust removal and mist removal unit II, and the fine liquid droplets and particles in the flue gas are strongly charged twice in the electrostatic dust removal and mist removal unit III. Due to the charging effect, the fine droplets and particles are adsorbed by the anode plate 7 for dust and fog removal, so that they are not carried by the air flow. After the fine droplets and particles gather on the surface of the anode plate, they flow down into the box along the surface of the anode plate by gravity The bottom of the body 2 is discharged from the sewage outlet 9. The purified flue gas is discharged from the flue gas outlet 8 up to the standard, and the deep dust and fog removal of the desulfurized flue gas is completed. the
本装置运行过程中,除尘除雾阳极板7可配备冲洗系统,可采用喷嘴喷射方式冲洗,提高除尘除雾阳极板7表面的收污效率。 During the operation of the device, the anode plate 7 for dedusting and demisting can be equipped with a flushing system, which can be rinsed by spraying nozzles to improve the efficiency of collecting dirt on the surface of the anode plate 7 for dedusting and demisting. the
实施例2Example 2
火力发电厂石灰石-石膏湿法烟气脱硫尾端烟气深度净化试验。 Deep purification test of flue gas at the tail end of limestone-gypsum wet flue gas desulfurization in thermal power plant.
如图4,脱硫塔12的尾端烟气出口烟道14连接烟卤19,同时引接旁路烟道13。将复合除尘除雾装置(以箱体2表示)连接在旁路烟道13的管路中。 As shown in Fig. 4, the flue gas outlet flue 14 at the tail end of the desulfurization tower 12 is connected to the smoke halogen 19, and at the same time leads to the bypass flue 13. Connect the composite dust and mist removal device (represented by box 2 ) to the pipeline of bypass flue 13 . the
箱体2横截面积为42 m2(6mX7m),装置长度为2 m(不包括进出口部位的喇叭状面积)。聚尘阳极板4材质为不锈钢,尺寸为500X6000 mm,两块阳极板间距为400 mm。阴极线3材质为不锈钢。收集板5布置间距为100 mm。阴极线6材质为不锈钢。阳极板7材质为纤维织物,单片纤维织物尺寸为250X6000 mm,两片纤维织物夹角为90 oC,板间距为100 mm。 The cross-sectional area of the box body 2 is 42 m 2 (6mX7m), and the length of the device is 2 m (excluding the trumpet-shaped area of the inlet and outlet). The material of the dust-collecting anode plate 4 is stainless steel, the size is 500×6000 mm, and the distance between the two anode plates is 400 mm. The cathode wire 3 is made of stainless steel. The collecting plates 5 are arranged at a spacing of 100 mm. The cathode wire 6 is made of stainless steel. The anode plate 7 is made of fiber fabric, the size of a single piece of fiber fabric is 250X6000 mm, the angle between two pieces of fiber fabric is 90 o C, and the distance between the plates is 100 mm.
从脱硫塔12出口的烟气温度为50~55 oC,烟气含尘量:40 mg/Nm3;含液滴量:75 mg/Nm3。试验中,开启挡板门15、挡板门17和挡板门19,挡板门16根据试验要求为部分或全部关闭,使脱硫塔12的尾端烟气从旁路烟道13通过复合除尘除雾装置(箱体)2,经深度净化后通入烟卤19排放。试验过程:调节挡板门16的开度,以改变进入旁路烟道13的烟气流量,分别在复合除尘除雾装置箱体2的出口测得深度净化后烟气含尘量和液滴量数据如下: The flue gas temperature at the outlet of the desulfurization tower 12 is 50~55 o C, the dust content of the flue gas: 40 mg/Nm 3 ; the liquid droplet content: 75 mg/Nm 3 . During the test, the baffle door 15, the baffle door 17 and the baffle door 19 were opened, and the baffle door 16 was partially or completely closed according to the test requirements, so that the flue gas at the tail end of the desulfurization tower 12 was passed through the composite dust collector through the bypass flue 13. The demisting device (cabinet) 2 is passed into the smoke halogen 19 to discharge after deep purification. Test process: Adjust the opening of the baffle door 16 to change the flue gas flow rate entering the bypass flue 13, and measure the dust content and liquid droplets of the deeply purified flue gas at the exit of the composite dust and mist removal device box 2 respectively. Quantitative data are as follows:
(1)旁路烟道13的烟气流量为620000 m3/h,复合除尘除雾装置箱体2内的烟气流速为4.1 m/s,出口烟气含尘量<20 mg/Nm3,含液滴量<20 mg/Nm3。 (1) The flue gas flow rate of the bypass flue 13 is 620,000 m 3 /h, the flue gas flow rate in the composite dust and mist removal device box 2 is 4.1 m/s, and the dust content of the flue gas at the outlet is less than 20 mg/Nm 3 , containing droplets <20 mg/Nm 3 .
(2)旁路烟道13的烟气流量为1162500 m3/h,复合除尘除雾装置箱体2内的烟气流速为7.7 m/s,出口烟气含尘量<30 mg/Nm3,含液滴量<20 mg/Nm3。 (2) The flue gas flow rate of the bypass flue 13 is 1,162,500 m 3 /h, the flue gas flow rate in the composite dust and mist removal device box 2 is 7.7 m/s, and the dust content of the flue gas at the outlet is less than 30 mg/Nm 3 , containing droplets <20 mg/Nm 3 .
(3)旁路烟道13的烟气流量为1550000 m3/h,复合除尘除雾装置箱体2内的烟气流速为10.3 m/s,出口烟气含尘量<30 mg/Nm3,含液滴量<30 mg/Nm3。 (3) The flue gas flow rate of the bypass flue 13 is 1,550,000 m 3 /h, the flue gas flow rate in the composite dust and mist removal device box 2 is 10.3 m/s, and the dust content of the flue gas at the outlet is less than 30 mg/Nm 3 , containing droplets <30 mg/Nm 3 .
从以上试验数据可知,复合除尘除雾装置能对湿法脱硫尾端烟气进行深度净化,进一步除去烟气中残留的尘粒和液滴(包括石膏浆液),因而确保烟气排放达标。 From the above test data, it can be seen that the composite dedusting and demisting device can deeply purify the flue gas at the end of wet desulfurization, and further remove residual dust particles and liquid droplets (including gypsum slurry) in the flue gas, thus ensuring that the flue gas emission meets the standard. the
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Cited By (4)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN103933813A (en) * | 2014-04-01 | 2014-07-23 | 国电环境保护研究院 | Combined dust removing and defogging device for smoke |
| CN107051097A (en) * | 2017-06-19 | 2017-08-18 | 孙时泽 | A kind of novel dust removing cleaner |
| CN107519721A (en) * | 2017-09-30 | 2017-12-29 | 无锡赛孚电力环境控制设备有限公司 | A kind of compound air intake dust arrester for transformer station's ventilating system |
| CN112756112A (en) * | 2021-01-19 | 2021-05-07 | 国电环境保护研究院有限公司 | Dry-type electric dust remover for high-efficiency dust removal through multi-region coupling |
-
2014
- 2014-04-01 CN CN201420153725.XU patent/CN203777877U/en not_active Expired - Lifetime
Cited By (4)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN103933813A (en) * | 2014-04-01 | 2014-07-23 | 国电环境保护研究院 | Combined dust removing and defogging device for smoke |
| CN107051097A (en) * | 2017-06-19 | 2017-08-18 | 孙时泽 | A kind of novel dust removing cleaner |
| CN107519721A (en) * | 2017-09-30 | 2017-12-29 | 无锡赛孚电力环境控制设备有限公司 | A kind of compound air intake dust arrester for transformer station's ventilating system |
| CN112756112A (en) * | 2021-01-19 | 2021-05-07 | 国电环境保护研究院有限公司 | Dry-type electric dust remover for high-efficiency dust removal through multi-region coupling |
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