CN110026036A - Flue gas aerosol removing means - Google Patents
Flue gas aerosol removing means Download PDFInfo
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- CN110026036A CN110026036A CN201910435360.7A CN201910435360A CN110026036A CN 110026036 A CN110026036 A CN 110026036A CN 201910435360 A CN201910435360 A CN 201910435360A CN 110026036 A CN110026036 A CN 110026036A
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D47/00—Separating dispersed particles from gases, air or vapours by liquid as separating agent
- B01D47/06—Spray cleaning
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D47/00—Separating dispersed particles from gases, air or vapours by liquid as separating agent
- B01D47/14—Packed scrubbers
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D53/00—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
- B01D53/14—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols by absorption
- B01D53/1406—Multiple stage absorption
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D53/00—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
- B01D53/14—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols by absorption
- B01D53/1425—Regeneration of liquid absorbents
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D53/00—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
- B01D53/14—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols by absorption
- B01D53/18—Absorbing units; Liquid distributors therefor
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2247/00—Details relating to the separation of dispersed particles from gases, air or vapours by liquid as separating agent
- B01D2247/04—Regenerating the washing fluid
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2247/00—Details relating to the separation of dispersed particles from gases, air or vapours by liquid as separating agent
- B01D2247/10—Means for removing the washing fluid dispersed in the gas or vapours
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2258/00—Sources of waste gases
- B01D2258/02—Other waste gases
- B01D2258/0283—Flue gases
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Abstract
本发明提供了一种烟气气溶胶脱除装置。该装置包括增湿单元和气溶胶脱除塔,增湿单元具有脱硫塔净烟气进口;气溶胶脱除塔由下至上依次包括第一气溶胶水洗段、第二气溶胶水洗段及除雾器,第一气溶胶水洗段下部设置有增湿烟气进口,其与增湿单元的出口相连。增湿单元先对脱硫净烟气进行增湿,能够使烟气达到过饱和状态。烟气被过饱和后,烟气中的少量灰尘、浆液颗粒直径会增大,增径后的微粒容易被循环水溶液溶解吸收。然后,利用气溶胶脱除塔先后对增湿烟气进行两次水洗,烟气中的气溶胶在气液碰撞接触中被溶解到水溶液中而被脱除。利用上述装置脱除脱硫烟气中的气溶胶,整体工艺简洁,投资小,工期短,且能够实现气溶胶超低排放。
The invention provides a flue gas aerosol removing device. The device includes a humidification unit and an aerosol removal tower, the humidification unit has a clean flue gas inlet of the desulfurization tower; the aerosol removal tower includes a first aerosol water washing section, a second aerosol water washing section and a mist eliminator in sequence from bottom to top , the lower part of the first aerosol water washing section is provided with a humidified flue gas inlet, which is connected with the outlet of the humidification unit. The humidification unit first humidifies the desulfurized clean flue gas, which can make the flue gas reach a supersaturated state. After the flue gas is supersaturated, the diameter of a small amount of dust and slurry particles in the flue gas will increase, and the increased diameter particles are easily dissolved and absorbed by the circulating aqueous solution. Then, the humidified flue gas is washed twice by the aerosol removal tower, and the aerosol in the flue gas is dissolved into the aqueous solution in the gas-liquid collision contact and removed. Using the above device to remove aerosols in the desulfurization flue gas has the advantages of simple overall process, small investment, short construction period and ultra-low emission of aerosols.
Description
技术领域technical field
本发明涉及烟气净化技术领域,具体而言,涉及一种烟气气溶胶脱除装置。The invention relates to the technical field of flue gas purification, in particular to a flue gas aerosol removal device.
背景技术Background technique
随着国家环保标准的日益提高,在用锅炉烟气脱硫装置烟气相继进行了脱硫脱硝改造,脱硫工艺基本可以分为干法、半干法和湿法工艺,多数工厂采样了湿法脱硫工艺,大型电厂主要采用石灰石石膏法,中小型锅炉更多的采用了氨法脱硫工艺,由于先期部分氨法脱硫技术本身的缺陷,脱硫后烟气气溶胶排放浓度居高不下,造成新的环境污染。With the increasing improvement of national environmental protection standards, the flue gas of in-use boiler flue gas desulfurization devices has been subjected to desulfurization and denitrification transformation. The desulfurization process can basically be divided into dry, semi-dry and wet processes. Most factories sample the wet desulfurization process. , Large-scale power plants mainly use limestone gypsum method, and small and medium-sized boilers use ammonia desulfurization technology. Due to the defects of some ammonia desulfurization technology in the early stage, the emission concentration of flue gas aerosol after desulfurization remains high, causing new environmental pollution. .
采用氨法脱硫工艺,烟气经过多级浆液喷淋吸收,得到净化后经烟囱排放至大气。由于脱硫工艺喷淋吸收浆液pH、浆液浓度、喷淋密度、氧化程度等指标的控制波动,未脱除干净的SO2和逃逸的游离NH3会在烟气中形成颗粒度极小的气溶胶;同时烟气经过喷淋层,喷嘴雾化出的极细微浆液雾滴随同被气流夹带,烟气中此部分气溶胶形式的颗粒物直径一般小于0.1微米,不能被安置于塔顶的常规除雾器所脱除,而被排放到大气中。Using ammonia desulfurization process, the flue gas is sprayed and absorbed by multi-stage slurry, purified and then discharged to the atmosphere through the chimney. Due to the controlled fluctuation of the desulfurization process spray absorption slurry pH, slurry concentration, spray density, oxidation degree and other indicators, the unremoved SO 2 and escaped free NH 3 will form aerosols with extremely small particle size in the flue gas At the same time, the flue gas passes through the spray layer, and the extremely fine slurry droplets atomized by the nozzle are entrained by the airflow. The diameter of the particles in the form of aerosols in the flue gas is generally less than 0.1 microns, which cannot be placed on the top of the tower. Conventional defogging removed by the device and discharged into the atmosphere.
常规氨法脱硫工艺,会在喷淋吸收层上部设计有除雾器,但除雾器只能脱除15微米以上的大颗粒,气溶胶无法脱除;有些先进氨法脱硫工艺通过控制最上层吸收段喷淋浆液的pH为酸性,从而阻止氨逃逸,降低气溶胶的生成,但效率有限,且无法阻止气相中夹带的细微浆液颗粒;有脱硫工艺在塔内除雾器下部增加超声波聚集增径段,使部分细微颗粒直径增大而被除雾器脱除,但效率一般只有30%,不能有效降低气溶胶在排放烟气中的浓度。In the conventional ammonia desulfurization process, a mist eliminator is designed on the upper part of the spray absorption layer, but the mist eliminator can only remove large particles above 15 microns, and the aerosol cannot be removed; some advanced ammonia desulfurization processes control the top layer by controlling the mist eliminator. The pH of the sprayed slurry in the absorption section is acidic, which prevents the escape of ammonia and reduces the generation of aerosols, but the efficiency is limited, and the fine slurry particles entrained in the gas phase cannot be prevented; there is a desulfurization process in the lower part of the tower. Diameter section, which increases the diameter of some fine particles and is removed by the mist eliminator, but the efficiency is generally only 30%, which cannot effectively reduce the concentration of aerosol in the exhaust gas.
另有工艺采取了脱硫塔后设置电除尘装置,对气溶胶脱除率较高,但是要达到超净排放,电除尘装置规模庞大、投资费用高,耗电量巨大,维护复杂。In another process, an electrostatic precipitator is installed after the desulfurization tower, which has a high removal rate of aerosols. However, to achieve ultra-clean emission, the electrostatic precipitator is large in scale, high in investment cost, huge in power consumption and complicated in maintenance.
发明内容SUMMARY OF THE INVENTION
本发明的主要目的在于提供一种烟气气溶胶脱除装置,以解决现有技术中脱硫后的烟气气溶胶去除率低或工序复杂、耗资大的问题。The main purpose of the present invention is to provide a flue gas aerosol removal device, so as to solve the problems of low removal rate of flue gas aerosol after desulfurization, complicated procedures and high cost in the prior art.
为了实现上述目的,根据本发明的一个方面,提供了一种烟气气溶胶脱除装置,其包括:增湿单元,具有脱硫塔净烟气进口;气溶胶脱除塔,由下至上依次包括第一气溶胶水洗段、第二气溶胶水洗段及除雾器,第一气溶胶水洗段下部设置有增湿烟气进口,其与增湿单元的出口相连。In order to achieve the above object, according to an aspect of the present invention, a flue gas aerosol removal device is provided, which includes: a humidification unit, which has a clean flue gas inlet of a desulfurization tower; an aerosol removal tower, which sequentially includes from bottom to top The first aerosol water washing section, the second aerosol water washing section and the demister are provided with a humidified flue gas inlet at the lower part of the first aerosol water washing section, which is connected with the outlet of the humidification unit.
进一步地,第一气溶胶水洗段为空塔分布水洗段或填料层水洗段;第二气溶胶水洗段为填料层水洗段。Further, the first aerosol washing section is an empty tower distribution washing section or a packing layer washing section; the second aerosol washing section is a packing layer washing section.
进一步地,气溶胶脱除塔还包括位于第一气溶胶水洗段下方的循环液槽。Further, the aerosol removal tower also includes a circulating liquid tank located below the first aerosol water washing section.
进一步地,当第一气溶胶水洗段为填料层水洗段时,气溶胶脱除塔还包括气体分布器,气体分布器设置在第一气溶胶水洗段和循环液槽之间,且气体分布器具有增湿烟气进口。Further, when the first aerosol washing section is the packing layer washing section, the aerosol removal tower also includes a gas distributor, and the gas distributor is arranged between the first aerosol washing section and the circulating liquid tank, and the gas distributor With humidified flue gas inlet.
进一步地,第一气溶胶水洗段包括第一水洗水分布器,第一水洗水分布器设置在第一气溶胶水洗段顶部;第二气溶胶水洗段包括第二水洗水分布器,第二水洗水分布器设置在第二气溶胶水洗段顶部。Further, the first aerosol washing section includes a first washing water distributor, and the first washing water distributor is arranged on the top of the first aerosol washing section; the second aerosol washing section includes a second washing water distributor, and the second washing water A water distributor is placed on top of the second aerosol water wash section.
进一步地,当第一气溶胶水洗段为填料层水洗段时,其还包括设置在第一水洗水分布器下方的第一填料层和用于支撑第一填料层的第一支撑部;第二气溶胶水洗段还包括位于第二水洗水分布器下方的第二填料层和用于支撑第二填料层的第二支撑部。Further, when the first aerosol washing section is a packing layer washing section, it further includes a first packing layer disposed below the first washing water distributor and a first supporting portion for supporting the first packing layer; the second The aerosol water washing section further includes a second packing layer located under the second washing water distributor and a second supporting part for supporting the second packing layer.
进一步地,第一气溶胶水洗段还包括位于第一支撑部下方的第一水洗升气式集液槽,第二气溶胶水洗段还包括位于第二支撑部下方的第二水洗升气式集液槽。Further, the first aerosol water washing section further includes a first water washing lift-type liquid collecting tank located below the first support part, and the second aerosol water washing section further includes a second water washing lift-type liquid collecting tank located under the second support part. tank.
进一步地,第一水洗水分布器设置有第一水洗水进口,循环液槽设置有循环水出口,循环水出口与第一水洗水进口通过第一循环管路相连,且第一循环管路上设置有第一循环泵;第二气溶胶水洗段设置有第二水洗水进口,第二水洗水进口与第二水洗升气式集液槽的出口通过第二循环管路相连,且第二循环管路上还设置有第二循环泵。Further, the first washing water distributor is provided with a first washing water inlet, the circulating liquid tank is provided with a circulating water outlet, and the circulating water outlet is connected with the first washing water inlet through a first circulating pipeline, and the first circulating pipeline is provided with There is a first circulating pump; the second aerosol washing section is provided with a second washing water inlet, and the second washing water inlet is connected with the outlet of the second washing air-lifting liquid collecting tank through a second circulation pipeline, and the second circulation pipe There is also a second circulating pump on the road.
进一步地,气溶胶脱除塔还包括:排放支管,与第一循环管路相连,且排放支管上设置有排液泵;循环旁路,其进口与第二循环管路相连,其出口与第一循环管路相连,且循环旁路上还设置有第三循环泵。Further, the aerosol removal tower also includes: a discharge branch pipe, which is connected to the first circulation pipeline, and a drain pump is arranged on the discharge branch pipe; A circulating pipeline is connected, and a third circulating pump is also arranged on the circulating bypass.
进一步地,第一填料层和第二填料层中采用的填料为球形填料、矩鞍环填料、阶梯环填料、格栅填料中的一种或多种,第一填料层和第二填料层分别为散装型填料层或规整型填料层。Further, the fillers used in the first packing layer and the second packing layer are one or more of spherical packing, saddle ring packing, stepped ring packing and grid packing, and the first packing layer and the second packing layer are respectively It is a bulk packing layer or a structured packing layer.
进一步地,增湿单元包括:进气烟道,具有脱硫塔净烟气进口,且进气烟道的出口与增湿烟气进口相连;增湿喷头,设置在进气烟道的内部。Further, the humidification unit includes: an intake flue with a clean flue gas inlet of the desulfurization tower, and the outlet of the intake flue is connected to the humidified flue gas inlet; a humidification nozzle is arranged inside the intake flue.
进一步地,除雾器为屋脊式除雾器、丝网除雾器或旋流式除雾器。Further, the mist eliminator is a roof type mist eliminator, a wire mesh mist eliminator or a cyclone mist eliminator.
进一步地,气溶胶脱除塔具有顶部排气口,气溶胶脱除塔还包括与顶部排气口相连的排气烟道,除雾器垂直设置在第二气溶胶水洗段的上方,或者,除雾器水平设置在排气烟道中。Further, the aerosol removal tower has a top exhaust port, the aerosol removal tower also includes an exhaust flue that is connected to the top exhaust port, and the mist eliminator is vertically arranged above the second aerosol water washing section, or, The mist eliminator is placed horizontally in the exhaust flue.
本发明提供的烟气气溶胶脱除装置包括增湿单元和气溶胶脱除塔,气溶胶脱除塔由下至上依次包括第一气溶胶水洗段、第二气溶胶水洗段及除雾器,第一气溶胶水洗段下部设置有增湿烟气进口,其与增湿单元的出口相连。增湿单元先对脱硫净烟气进行增湿,能够使烟气达到过饱和状态。烟气被过饱和后,烟气中的少量灰尘、浆液颗粒直径会增大,增径后的微粒容易被循环水溶液溶解吸收。然后,利用气溶胶脱除塔先后对增湿烟气进行两次水洗,烟气中的气溶胶在气液碰撞接触中被溶解吸收到水溶液中而被脱除,然后,利用除雾器进一步除雾,排放The flue gas aerosol removal device provided by the present invention includes a humidification unit and an aerosol removal tower. The aerosol removal tower sequentially includes a first aerosol water washing section, a second aerosol water washing section and a mist eliminator from bottom to top. The lower part of an aerosol water washing section is provided with a humidified flue gas inlet, which is connected with the outlet of the humidification unit. The humidification unit first humidifies the desulfurized clean flue gas, which can make the flue gas reach a supersaturated state. After the flue gas is supersaturated, the diameter of a small amount of dust and slurry particles in the flue gas will increase, and the increased diameter particles are easily dissolved and absorbed by the circulating aqueous solution. Then, the humidified flue gas was washed twice by the aerosol removal tower, and the aerosol in the flue gas was dissolved and absorbed into the aqueous solution in the gas-liquid collision contact to be removed. Then, the mist eliminator was used to further remove fog, emission
利用上述装置脱除脱硫烟气中的气溶胶,整体工艺简洁,方便现有脱硫工艺改造,并能够与现有脱硫工艺结合,投资小,工期短,实现气溶胶超低排放。同时,该装置具有很强的变负荷适应能力,对气溶胶脱除的同时也脱除了烟气中的粉尘、进一步降低了烟气SO2浓度。Using the above device to remove aerosols in the desulfurization flue gas, the overall process is simple, convenient for the transformation of the existing desulfurization process, and can be combined with the existing desulfurization process, the investment is small, the construction period is short, and the ultra-low emission of aerosols is realized. At the same time, the device has a strong ability to adapt to variable loads, removes the aerosol and also removes the dust in the flue gas, and further reduces the SO 2 concentration of the flue gas.
附图说明Description of drawings
构成本申请的一部分的说明书附图用来提供对本发明的进一步理解,本发明的示意性实施例及其说明用于解释本发明,并不构成对本发明的不当限定。在附图中:The accompanying drawings forming a part of the present application are used to provide further understanding of the present invention, and the exemplary embodiments of the present invention and their descriptions are used to explain the present invention and do not constitute an improper limitation of the present invention. In the attached image:
图1示出了根据本发明一种实施例的烟气气溶胶脱除装置结构示意图;FIG. 1 shows a schematic structural diagram of a device for removing flue gas aerosol according to an embodiment of the present invention;
图2示出了根据本发明另一种实施例的烟气气溶胶脱除装置结构示意图;以及FIG. 2 shows a schematic structural diagram of a device for removing flue gas aerosol according to another embodiment of the present invention; and
图3示出了根据本发明又一种实施例的烟气气溶胶脱除装置结构示意图。FIG. 3 shows a schematic structural diagram of a device for removing flue gas aerosol according to yet another embodiment of the present invention.
其中,上述附图包括以下附图标记:Wherein, the above-mentioned drawings include the following reference signs:
10、增湿单元;11、进气烟道;12、增湿喷头;20、气溶胶脱除塔;21、第一气溶胶水洗段;211、第一水洗水分布器;212、第一填料层;213、第一支撑部;214、第一水洗升气式集液槽;22、第二气溶胶水洗段;221、第二水洗水分布器;222、第二填料层;223、第二支撑部;224、第二水洗升气式集液槽;23、除雾器;24、气体分布器;25、循环液槽;26、排气烟道;201、第一循环泵;202、第二循环泵;203、排液泵;204、第三循环泵;10. Humidification unit; 11. Intake flue; 12. Humidification nozzle; 20. Aerosol removal tower; 21. First aerosol washing section; 211. First washing water distributor; 212, First packing layer; 213, the first support part; 214, the first water washing lift-type liquid collecting tank; 22, the second aerosol washing section; 221, the second washing water distributor; 222, the second packing layer; 223, the second Supporting part; 224, the second water-washing lift-type liquid collecting tank; 23, the mist eliminator; 24, the gas distributor; 25, the circulating liquid tank; 26, the exhaust flue; 201, the first circulating pump; 202, the first The second circulation pump; 203, the discharge pump; 204, the third circulation pump;
1、脱硫净化气排气烟道;2、烟囱;101、第一隔板;3、第二隔板;205、第三隔板。1. Desulfurization and purification gas exhaust flue; 2. Chimney; 101. The first separator; 3. The second separator; 205, The third separator.
具体实施方式Detailed ways
需要说明的是,在不冲突的情况下,本申请中的实施例及实施例中的特征可以相互组合。下面将参考附图并结合实施例来详细说明本发明。It should be noted that the embodiments in the present application and the features of the embodiments may be combined with each other in the case of no conflict. The present invention will be described in detail below with reference to the accompanying drawings and in conjunction with the embodiments.
正如背景技术部分所描述的,目前脱硫后的烟气气溶胶去除率低或工序复杂、耗资大。As described in the background art section, the current flue gas aerosol removal rate after desulfurization is low or the process is complicated and expensive.
为了解决这一问题,本发明提供了一种烟气气溶胶脱除装置,如图1至3所示,该装置包括:增湿单元10,具有脱硫塔净烟气进口;气溶胶脱除塔20,由下至上依次包括第一气溶胶水洗段21、第二气溶胶水洗段22及除雾器23,第一气溶胶水洗段21下部设置有增湿烟气进口,其与增湿单元10的出口相连。In order to solve this problem, the present invention provides a flue gas aerosol removal device, as shown in Figures 1 to 3, the device includes: a humidification unit 10, which has a clean flue gas inlet of a desulfurization tower; an aerosol removal tower 20, including the first aerosol washing section 21, the second aerosol washing section 22 and the mist eliminator 23 in sequence from bottom to top, the lower part of the first aerosol washing section 21 is provided with a humidifying flue gas inlet, which is connected with the humidifying unit 10 connected to the outlet.
增湿单元10先对脱硫净烟气A进行增湿,能够使烟气达到过饱和状态。烟气被过饱和后,烟气中的少量灰尘、浆液颗粒直径会增大,增径后的微粒容易被循环水溶液溶解吸收。然后,利用气溶胶脱除塔20先后对增湿烟气进行两次水洗,烟气中的气溶胶在气液碰撞接触中被溶解吸收到水溶液中而被脱除,然后,利用除雾器23进一步除雾,排放。利用上述装置脱除脱硫烟气中的气溶胶,整体工艺简洁,方便现有脱硫工艺改造,并能够与现有脱硫工艺结合,投资小,工期短,实现气溶胶超低排放。同时,该装置具有很强的变负荷适应能力,对气溶胶脱除的同时也脱除了烟气中的粉尘、进一步降低了烟气SO2浓度。The humidification unit 10 first humidifies the desulfurized clean flue gas A, so that the flue gas can reach a supersaturated state. After the flue gas is supersaturated, the diameter of a small amount of dust and slurry particles in the flue gas will increase, and the increased diameter particles are easily dissolved and absorbed by the circulating aqueous solution. Then, the humidified flue gas is washed twice by the aerosol removal tower 20, and the aerosol in the flue gas is dissolved and absorbed into the aqueous solution in the gas-liquid collision contact to be removed, and then the mist eliminator 23 is used. Further defogging, discharge. Using the above device to remove aerosols in the desulfurization flue gas, the overall process is simple, convenient for the transformation of the existing desulfurization process, and can be combined with the existing desulfurization process, the investment is small, the construction period is short, and the ultra-low emission of aerosols is realized. At the same time, the device has a strong ability to adapt to variable loads, removes the aerosol and also removes the dust in the flue gas, and further reduces the SO 2 concentration of the flue gas.
在一种优选的实施例中,第一气溶胶水洗段21为空塔分布水洗段(如图2所示)或填料层水洗段(如图1所示);第二气溶胶水洗段22为填料层水洗段。当第一气溶胶水洗段21为空塔分布水洗段时,增湿烟气在进入后有足够的时间和空间进行气相均匀分布,并完成第一阶段的水洗,去除脱硫烟气中的大部分灰尘、气溶胶。接着进入第二阶段的填料层水洗段进行进一步水洗,采用填料层,气液接触充分,气溶胶溶解充分,二次夹带量小,有利于进一步降低气溶胶含量,并降低对于除雾器23的要求。最后,经二次水洗后的烟气通过除雾器23除去烟气所携带的液滴后,净化气得以排放。当第一气溶胶水洗段21为填料层水洗段时,增湿烟气先进入第一气溶胶水洗段21的填料层,填料层形成水膜,实现水膜预吸收功能;预洗后的烟气进入第二气溶胶水洗段22的填料层,实现水膜的精吸收。In a preferred embodiment, the first aerosol washing section 21 is an empty tower distribution washing section (as shown in FIG. 2 ) or a packing layer washing section (as shown in FIG. 1 ); the second aerosol washing section 22 is The packing layer is washed with water. When the first aerosol water washing section 21 is an empty tower distribution water washing section, the humidified flue gas has enough time and space to distribute the gas phase evenly after entering, and the first stage of water washing is completed to remove most of the desulfurization flue gas. Dust, aerosols. Then enter the water washing section of the packing layer in the second stage for further water washing, using the packing layer, the gas-liquid contact is sufficient, the aerosol is fully dissolved, and the secondary entrainment amount is small, which is conducive to further reducing the aerosol content and reducing the impact on the mist eliminator 23. Require. Finally, after the flue gas after the secondary water washing passes through the mist eliminator 23 to remove the droplets carried by the flue gas, the purified gas is discharged. When the first aerosol washing section 21 is a packing layer washing section, the humidified flue gas first enters the packing layer of the first aerosol washing section 21, and the packing layer forms a water film to realize the pre-absorption function of the water film; The gas enters the packing layer of the second aerosol water washing section 22 to realize the fine absorption of the water film.
为了收集水洗水并将其循环利用,在一种优选的实施例中,气溶胶脱除塔20还包括位于第一气溶胶水洗段21下方的循环液槽25。更优选地,当第一气溶胶水洗段21为填料层水洗段时,气溶胶脱除塔20还包括气体分布器24,气体分布器24设置在第一气溶胶水洗段21和循环液槽25之间,且气体分布器24具有增湿烟气进口。利用气体分布器24能够使增湿烟气更均匀地进入并与水洗水接触。且需要说明的是,当第一气溶胶水洗段21为空塔分布水洗段时,因增湿烟气在进入后有足够的时间和空间进行气相均匀分布,无需设置气体分布器。而且,该种设置方式更适宜处理粉尘含量(主要是硫酸铵固体胶体)不高的烟气,采用该方式时气溶胶脱除塔的压降较两层填料水洗时有所降低,在锅炉引风机压头裕量不足时可以考虑采用该类型。In order to collect and recycle the washing water, in a preferred embodiment, the aerosol removal tower 20 further includes a circulating liquid tank 25 located below the first aerosol washing section 21 . More preferably, when the first aerosol washing section 21 is a packing layer washing section, the aerosol removal tower 20 further includes a gas distributor 24, and the gas distributor 24 is arranged in the first aerosol washing section 21 and the circulating liquid tank 25. between, and the gas distributor 24 has a humidified flue gas inlet. The use of the gas distributor 24 enables the humidified flue gas to enter and contact the wash water more uniformly. It should be noted that, when the first aerosol washing section 21 is an empty tower distribution washing section, since the humidified flue gas has enough time and space for uniform gas phase distribution after entering, no gas distributor is required. Moreover, this setting method is more suitable for processing flue gas with low dust content (mainly ammonium sulfate solid colloid). When this method is used, the pressure drop of the aerosol removal tower is lower than that of the two-layer packing with water. This type can be considered when the head margin of the fan is insufficient.
在一种优选的实施例中,第一气溶胶水洗段21包括第一水洗水分布器211,第一水洗水分布器211设置在第一气溶胶水洗段21顶部;第二气溶胶水洗段22包括第二水洗水分布器221,第二水洗水分布器221设置在第二气溶胶水洗段22顶部。这样,增湿烟气从塔底部进入后,先后两次与水洗水逆流接触,有利于进一步提高气溶胶、灰尘等的去除效果。且利用水洗水分布器能够使水洗水均匀分布到填料层。In a preferred embodiment, the first aerosol washing section 21 includes a first washing water distributor 211, and the first washing water distributor 211 is arranged at the top of the first aerosol washing section 21; the second aerosol washing section 22 The second washing water distributor 221 is included, and the second washing water distributor 221 is arranged at the top of the second aerosol washing section 22 . In this way, after the humidified flue gas enters from the bottom of the tower, it is in countercurrent contact with the washing water twice, which is beneficial to further improve the removal effect of aerosol and dust. And the use of the washing water distributor can make the washing water evenly distributed to the packing layer.
优选地,第一水洗水分布器211包括第一分布总管和与第一分布总管相连的多个第一分布支管;第二水洗水分布器221包括第二分布总管和与第二分布总管相连的多个第二分布支管。优选地,当第一气溶胶水洗段21为空塔分布水洗段时,第一分布支管为碳化硅螺旋喷嘴,向下方成雾罩形状喷射,形成液雾高度叠加的喷淋区,下降的水雾与上升的烟气形成逆向流,烟气中的粉尘(硫酸铵胶体)被水雾溶解、洗涤。Preferably, the first washing water distributor 211 includes a first distribution manifold and a plurality of first distribution branch pipes connected to the first distribution manifold; the second washing water distributor 221 includes a second distribution manifold and a plurality of first distribution manifolds connected to the second distribution manifold A plurality of second distribution branches. Preferably, when the first aerosol washing section 21 is an empty tower distribution washing section, the first distribution branch pipe is a silicon carbide spiral nozzle, which is sprayed downward in the shape of a mist hood to form a spray area with a highly superimposed liquid mist, and the falling water The mist and the rising flue gas form a reverse flow, and the dust (ammonium sulfate colloid) in the flue gas is dissolved and washed by the water mist.
在一种优选的实施例中,当第一气溶胶水洗段21为填料层水洗段时,其还包括设置在第一水洗水分布器211下方的第一填料层212和用于支撑第一填料层212的第一支撑部213;第二气溶胶水洗段22还包括位于第二水洗水分布器221下方的第二填料层222和用于支撑第二填料层222的第二支撑部223。更优选地,第一气溶胶水洗段21还包括位于第一支撑部213下方的第一水洗升气式集液槽214,第二气溶胶水洗段22还包括位于第二支撑部223下方的第二水洗升气式集液槽224。这样,增湿烟气进入后,穿过第一水洗升气式集液槽214进入第一填料层212,与水洗水接触后,进一步通过第二水洗水分布器221进入第二填料层222与水洗水接触。In a preferred embodiment, when the first aerosol washing section 21 is a packing layer washing section, it further includes a first packing layer 212 disposed under the first washing water distributor 211 and a first packing layer 212 for supporting the first packing The first support portion 213 of the layer 212 ; the second aerosol washing section 22 further includes a second packing layer 222 located below the second washing water distributor 221 and a second support portion 223 for supporting the second packing layer 222 . More preferably, the first aerosol washing section 21 further includes a first washing lift-type liquid collecting tank 214 located below the first support portion 213 , and the second aerosol washing section 22 further includes a second aerosol washing section 223 located below the second support portion 223 . Two water-washed lift-type liquid collecting tank 224. In this way, after the humidified flue gas enters, it enters the first packing layer 212 through the first water-washing air-lifting liquid collecting tank 214, and after contacting with the washing water, it further enters the second packing layer 222 and the second packing layer 222 through the second washing water distributor 221. Washing water contact.
为了使水洗水循环利用从而节约能源,在一种优选的实施例中,第一水洗水分布器211设置有第一水洗水进口,循环液槽25设置有循环水出口,循环水出口与第一水洗水进口通过第一循环管路相连,且第一循环管路上设置有第一循环泵201;第二气溶胶水洗段22设置有第二水洗水进口,第二水洗水进口与第二水洗升气式集液槽224的出口通过第二循环管路相连,且第二循环管路上还设置有第二循环泵202。在实际操作中,也可以实时向循环液槽25中补充水洗水。In order to recycle the washing water to save energy, in a preferred embodiment, the first washing water distributor 211 is provided with a first washing water inlet, the circulating liquid tank 25 is provided with a circulating water outlet, and the circulating water outlet is connected to the first washing water inlet. The water inlet is connected through a first circulation pipeline, and the first circulation pipeline is provided with a first circulation pump 201; the second aerosol washing section 22 is provided with a second washing water inlet, and the second washing water inlet is connected to the second washing water lift gas The outlet of the liquid collecting tank 224 is connected through a second circulation pipeline, and a second circulation pump 202 is also provided on the second circulation pipeline. In actual operation, the washing water can also be replenished into the circulating liquid tank 25 in real time.
在一种优选的实施方式中,气溶胶脱除塔20还包括:排放支管,与第一循环管路相连,且排放支管上设置有排液泵203;循环旁路,其进口与第二循环管路相连,其出口与第一循环管路相连,且循环旁路上还设置有第三循环泵204。在实际实施过程中,当第一气溶胶水洗段21中的循环水达到一定比重后,可以通过排放支管送给上游脱硫塔系统B,该比重优选控制在1.05~1.1之间;第二气溶胶水洗段22的循环水达到指定比重后,可以通过循环旁路送入第一气溶胶水洗段21中,第二气溶胶水洗段22的水洗水比重优选控制在1.0~1.05之间。In a preferred embodiment, the aerosol removal tower 20 further comprises: a discharge branch pipe, which is connected to the first circulation pipe, and a discharge pump 203 is arranged on the discharge branch pipe; a circulation bypass, the inlet of which is connected to the second circulation pipe The pipelines are connected, and the outlet is connected to the first circulation pipeline, and a third circulation pump 204 is also provided on the circulation bypass. In the actual implementation process, when the circulating water in the first aerosol washing section 21 reaches a certain specific gravity, it can be sent to the upstream desulfurization tower system B through the discharge branch pipe, and the specific gravity is preferably controlled between 1.05 and 1.1; the second aerosol After the circulating water in the washing section 22 reaches the specified specific gravity, it can be sent to the first aerosol washing section 21 through the circulating bypass. The specific gravity of the washing water in the second aerosol washing section 22 is preferably controlled between 1.0 and 1.05.
为了进一步提高气液接触效果从而进一步改善烟气处理效果,在一种优选的实施例中,第一填料层212和第二填料层222中采用的填料为球形填料、矩鞍环填料、阶梯环填料、格栅填料中的一种或多种,第一填料层212和第二填料层222分别为散装型填料层或规整型填料层。In order to further improve the gas-liquid contact effect and thus further improve the flue gas treatment effect, in a preferred embodiment, the fillers used in the first packing layer 212 and the second packing layer 222 are spherical packing, saddle ring packing, stepped ring packing One or more of packing and grid packing, the first packing layer 212 and the second packing layer 222 are respectively bulk packing layers or structured packing layers.
在一种优选的实施例中,增湿单元10包括:进气烟道11,具有脱硫塔净烟气进口,且进气烟道11的出口与增湿烟气进口相连;增湿喷头12,设置在进气烟道11的内部。在实际操作时,可以将进气烟道11与现有脱硫装置中本身已有的脱硫净化气排气烟道1相连,使脱硫净化气先进入本发明的进气烟道11中增湿后再进入气溶胶脱除塔20。处理后的净化气排入至已有的烟囱2中。In a preferred embodiment, the humidification unit 10 includes: an intake flue 11 with a clean flue gas inlet of the desulfurization tower, and the outlet of the intake flue 11 is connected to the humidified flue gas inlet; a humidification nozzle 12, It is arranged inside the intake flue 11 . In actual operation, the intake flue 11 can be connected with the existing desulfurization and purified gas exhaust flue 1 in the existing desulfurization device, so that the desulfurized and purified gas first enters the intake flue 11 of the present invention after humidification. Then enter the aerosol removal tower 20. The treated purified gas is discharged into the existing chimney 2 .
在一种优选的实施例中,除雾器23为屋脊式除雾器、丝网除雾器或旋流式除雾器。更优选地,气溶胶脱除塔20具有顶部排气口,气溶胶脱除塔20还包括与顶部排气口相连的排气烟道26,除雾器23垂直设置在第二气溶胶水洗段22的上方(如图1和2所示),或者,除雾器23水平设置在排气烟道中(如图3所示)。采用除雾器23水平设置在排气烟道中的方式,可有效降低塔高约两米左右,同时可以减轻塔的负载及降低施工工程量。且采用该种形式的除雾器布置后,其内部结构及冲洗形式均和垂直布置有所不同,除雾器23安装在水平烟道上,需要进行固定。In a preferred embodiment, the mist eliminator 23 is a roof ridge mist eliminator, a wire mesh mist eliminator or a cyclone mist eliminator. More preferably, the aerosol removal tower 20 has a top exhaust port, the aerosol removal tower 20 also includes an exhaust flue 26 connected to the top exhaust port, and the mist eliminator 23 is vertically arranged in the second aerosol water washing section. 22 (as shown in Figures 1 and 2), or, the mist eliminator 23 is arranged horizontally in the exhaust flue (as shown in Figure 3). By using the method of horizontally setting the mist eliminator 23 in the exhaust flue, the tower height can be effectively reduced by about two meters, and the load of the tower can be reduced and the amount of construction work can be reduced at the same time. And after adopting this type of demister arrangement, its internal structure and flushing form are different from the vertical arrangement. The demister 23 is installed on the horizontal flue and needs to be fixed.
优选地,上述进气烟道11中设置有第一隔板101,脱硫净化气排气烟道1中设置有第二隔板3,排气烟道26中设置有第三隔板205。设置各隔板可以便于检修。Preferably, the above-mentioned intake flue 11 is provided with a first partition 101 , the desulfurized purified gas exhaust flue 1 is provided with a second partition 3 , and the exhaust flue 26 is provided with a third partition 205 . The installation of each partition can facilitate maintenance.
在实际操作时,优选地,间歇性地采用冲洗水C对除雾器23进行冲洗,以将截流的液滴冲下,冲洗液下落后进入第二水洗水分布器221参与填料水洗。当然,如果烟气离开脱硫塔,气溶胶数量和颗粒大小能被脱出塔脱除时,就可以停用增湿,以节能;停用增湿会减少循环段补水,所以可以用生产水作为循环段补水设施。In actual operation, preferably, flushing water C is used to flush the mist eliminator 23 intermittently to flush down the intercepted liquid droplets. After the flushing liquid falls, it enters the second flushing water distributor 221 to participate in the packing water flushing. Of course, if the flue gas leaves the desulfurization tower, and the aerosol quantity and particle size can be removed by the extraction tower, humidification can be disabled to save energy; deactivation of humidification will reduce the water replenishment in the circulation section, so the production water can be used as the circulation Water supply facilities.
以上所述仅为本发明的优选实施例而已,并不用于限制本发明,对于本领域的技术人员来说,本发明可以有各种更改和变化。凡在本发明的精神和原则之内,所作的任何修改、等同替换、改进等,均应包含在本发明的保护范围之内。The above descriptions are only preferred embodiments of the present invention, and are not intended to limit the present invention. For those skilled in the art, the present invention may have various modifications and changes. Any modification, equivalent replacement, improvement, etc. made within the spirit and principle of the present invention shall be included within the protection scope of the present invention.
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| CN117323805A (en) * | 2023-11-14 | 2024-01-02 | 浙江天地环保科技股份有限公司 | Organic amine CO based on small molecule organic solvent 2 Absorbent emission control device |
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Application publication date: 20190719 |