CN104645812A - Purification method for tail gas of calcium carbide furnace - Google Patents
Purification method for tail gas of calcium carbide furnace Download PDFInfo
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- CN104645812A CN104645812A CN201510106010.8A CN201510106010A CN104645812A CN 104645812 A CN104645812 A CN 104645812A CN 201510106010 A CN201510106010 A CN 201510106010A CN 104645812 A CN104645812 A CN 104645812A
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- 239000005997 Calcium carbide Substances 0.000 title claims abstract description 31
- CLZWAWBPWVRRGI-UHFFFAOYSA-N tert-butyl 2-[2-[2-[2-[bis[2-[(2-methylpropan-2-yl)oxy]-2-oxoethyl]amino]-5-bromophenoxy]ethoxy]-4-methyl-n-[2-[(2-methylpropan-2-yl)oxy]-2-oxoethyl]anilino]acetate Chemical compound CC1=CC=C(N(CC(=O)OC(C)(C)C)CC(=O)OC(C)(C)C)C(OCCOC=2C(=CC=C(Br)C=2)N(CC(=O)OC(C)(C)C)CC(=O)OC(C)(C)C)=C1 CLZWAWBPWVRRGI-UHFFFAOYSA-N 0.000 title claims abstract description 31
- 238000000034 method Methods 0.000 title claims abstract description 26
- 238000000746 purification Methods 0.000 title claims abstract description 8
- 239000000428 dust Substances 0.000 claims abstract description 67
- 238000010521 absorption reaction Methods 0.000 claims abstract description 45
- 239000002245 particle Substances 0.000 claims abstract description 14
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims description 8
- 238000007664 blowing Methods 0.000 claims description 6
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical group [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 claims description 5
- 230000009471 action Effects 0.000 claims description 5
- 239000000835 fiber Substances 0.000 claims description 4
- 238000013016 damping Methods 0.000 claims description 3
- 239000003365 glass fiber Substances 0.000 claims description 3
- 239000004743 Polypropylene Substances 0.000 claims description 2
- 229910052751 metal Inorganic materials 0.000 claims description 2
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- 239000013618 particulate matter Substances 0.000 claims description 2
- -1 polypropylene Polymers 0.000 claims description 2
- 229920001155 polypropylene Polymers 0.000 claims description 2
- 230000008569 process Effects 0.000 abstract description 7
- 239000007787 solid Substances 0.000 abstract description 5
- 238000001035 drying Methods 0.000 abstract 2
- 230000000694 effects Effects 0.000 description 6
- 238000011069 regeneration method Methods 0.000 description 6
- 239000007788 liquid Substances 0.000 description 5
- 230000008929 regeneration Effects 0.000 description 5
- UGFAIRIUMAVXCW-UHFFFAOYSA-N Carbon monoxide Chemical compound [O+]#[C-] UGFAIRIUMAVXCW-UHFFFAOYSA-N 0.000 description 4
- 229910002091 carbon monoxide Inorganic materials 0.000 description 4
- 238000009826 distribution Methods 0.000 description 4
- 238000001914 filtration Methods 0.000 description 4
- LYCAIKOWRPUZTN-UHFFFAOYSA-N Ethylene glycol Chemical compound OCCO LYCAIKOWRPUZTN-UHFFFAOYSA-N 0.000 description 3
- 238000004519 manufacturing process Methods 0.000 description 3
- 238000001514 detection method Methods 0.000 description 2
- 238000010586 diagram Methods 0.000 description 2
- 239000012535 impurity Substances 0.000 description 2
- 239000000463 material Substances 0.000 description 2
- 239000003595 mist Substances 0.000 description 2
- 239000000126 substance Substances 0.000 description 2
- 239000004280 Sodium formate Substances 0.000 description 1
- 230000009286 beneficial effect Effects 0.000 description 1
- 230000003139 buffering effect Effects 0.000 description 1
- BRPQOXSCLDDYGP-UHFFFAOYSA-N calcium oxide Chemical compound [O-2].[Ca+2] BRPQOXSCLDDYGP-UHFFFAOYSA-N 0.000 description 1
- ODINCKMPIJJUCX-UHFFFAOYSA-N calcium oxide Inorganic materials [Ca]=O ODINCKMPIJJUCX-UHFFFAOYSA-N 0.000 description 1
- 239000000292 calcium oxide Substances 0.000 description 1
- 229910052799 carbon Inorganic materials 0.000 description 1
- 238000005516 engineering process Methods 0.000 description 1
- 239000003344 environmental pollutant Substances 0.000 description 1
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- 231100000719 pollutant Toxicity 0.000 description 1
- 238000004064 recycling Methods 0.000 description 1
- 230000002787 reinforcement Effects 0.000 description 1
- 238000007789 sealing Methods 0.000 description 1
- HLBBKKJFGFRGMU-UHFFFAOYSA-M sodium formate Chemical compound [Na+].[O-]C=O HLBBKKJFGFRGMU-UHFFFAOYSA-M 0.000 description 1
- 235000019254 sodium formate Nutrition 0.000 description 1
- 229910001220 stainless steel Inorganic materials 0.000 description 1
- 239000010935 stainless steel Substances 0.000 description 1
- 238000009827 uniform distribution Methods 0.000 description 1
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- Treating Waste Gases (AREA)
Abstract
Description
技术领域technical field
本发明涉及一种电石炉尾气的净化方法。The invention relates to a method for purifying tail gas of a calcium carbide furnace.
背景技术Background technique
电石生产一般在电石炉中进行,通过电弧产生高温,氧化钙与碳发生反生成碳化钙(电石)和一氧化碳。密闭式电石炉尾气中除含有大量的一氧化碳之外还含有大量的粉尘,例如每生产一吨电石可副产尾气量400立方米左右,电石炉尾气中主要含有CO、H2等,其中85%以上都是CO气体。对于电石炉尾气的处理,大多数企业都是火炬燃烧掉,这样即污染环境又浪费了一氧化碳资源,而一氧化碳可以用于制造甲酸钠、乙二醇等产品,具有很高的商业价值,应该得以有效的利用。如果需要利用电石炉尾气中的CO,则必须对电石炉尾气中含有的大量的粉尘进行处理,去除颗粒污染物之后得到洁净的CO为主的排气,然后再加以利用。目前已知的粉尘处理方式主要包括湿法处理和干法处理,这两种手段都具有各自的优缺点,现有的技术难以高效的去除电石炉尾气中的粉尘颗粒物,因此急需开发一种更为有效的技术手段以对尾气进行处理得到洁净的排气。Calcium carbide production is generally carried out in calcium carbide furnaces, where high temperatures are generated by electric arcs, and calcium oxide reacts with carbon to form calcium carbide (calcium carbide) and carbon monoxide. In addition to a large amount of carbon monoxide, the exhaust gas of the closed calcium carbide furnace also contains a large amount of dust. For example, about 400 cubic meters of exhaust gas can be produced by producing one ton of calcium carbide furnace. The exhaust gas of calcium carbide furnace mainly contains CO, H2, etc., of which 85% All of the above are CO gas. For the treatment of calcium carbide furnace tail gas, most enterprises burn it with torches, which pollutes the environment and wastes carbon monoxide resources. Carbon monoxide can be used to manufacture sodium formate, ethylene glycol and other products, which has high commercial value and should be effectively use. If it is necessary to utilize the CO in the exhaust gas of the calcium carbide furnace, a large amount of dust contained in the exhaust gas of the calcium carbide furnace must be treated to remove particulate pollutants to obtain a clean CO-based exhaust gas, which can then be utilized. The currently known dust treatment methods mainly include wet treatment and dry treatment, both of which have their own advantages and disadvantages. It is difficult for existing technologies to efficiently remove dust particles in the exhaust gas of calcium carbide furnaces. Therefore, it is urgent to develop a more It is an effective technical means to process the exhaust gas to obtain clean exhaust gas.
发明内容Contents of the invention
本发明的目的在于提供一种有效的工艺,去除电石炉尾气中的固体颗粒物,实现尾气的清洁排放。The object of the present invention is to provide an effective process for removing solid particles in the tail gas of a calcium carbide furnace, so as to realize clean discharge of the tail gas.
本发明解决其技术问题所采用的技术方案是:一种电石炉尾气的净化方法,包括湿法吸收步骤和干法除尘步骤,其特征在于:尾气首先进入吸收塔1,吸收塔气体入口2进入吸收塔1之后变为多个分支入口6,分支入口6从上至下沿斜线均匀分布在吸收塔内,最上方的分支入口距离气体入口2最近,最下方的分支入口距离气体入口2最远;在各个分支入口的上部均设有一对应的喷雾器5,各喷雾器5距离相对应的分支入口的距离为0.5-2m;喷雾器喷射的水捕捉电石炉尾气中的粉尘颗粒物后落入吸收塔底部,底部的水在循环泵7的作用下循环回喷雾器继续吸收除尘;The technical scheme adopted by the present invention to solve the technical problem is: a method for purifying calcium carbide furnace tail gas, including a wet absorption step and a dry dust removal step, characterized in that the tail gas first enters the absorption tower 1, and the gas inlet 2 of the absorption tower enters After the absorption tower 1, it becomes a plurality of branch inlets 6, and the branch inlets 6 are evenly distributed in the absorption tower along the oblique line from top to bottom. The uppermost branch inlet is the closest to the gas inlet 2, and the lowermost branch inlet is the furthest A corresponding sprayer 5 is arranged on the upper part of each branch entrance, and the distance between each sprayer 5 and the corresponding branch entrance is 0.5-2m; the water sprayed by the sprayer catches the dust particles in the exhaust gas of the calcium carbide furnace and falls into the bottom of the absorption tower , the water at the bottom is circulated back to the sprayer under the action of the circulation pump 7 to continue to absorb and remove dust;
从吸收塔1排出的尾气随后进入除尘器10内,尾气首先从除尘器入口11进入除尘器,尾气正面冲击在分流罩12上,分流罩为圆锥形体,大部分尾气经过渐扩段16进入除尘器扩充段17内的流动腔33,尾气经过流动腔33之后同滤芯支撑架29内的滤芯30接触,气体穿过滤芯30过滤后进入排气腔32排出除尘器;The exhaust gas discharged from the absorption tower 1 then enters the dust collector 10. The exhaust gas first enters the dust collector from the inlet 11 of the dust collector, and the exhaust gas impacts on the shunt cover 12 head-on. The flow chamber 33 in the device expansion section 17, the exhaust gas passes through the flow chamber 33 and contacts the filter element 30 in the filter element support frame 29, and the gas passes through the filter element 30 and is filtered and enters the exhaust chamber 32 to be discharged from the dust collector;
一小部分尾气撞击分流罩12之后沿着分流罩12向下流动,撞击到滤芯支撑架29上部顶板39上固定的3-10片叶片28,滤芯支撑架29内壁上设有螺旋滑道36,螺旋滑道36与环形内挡板15外壁的第二螺旋滑道配合,尾气撞击叶片28,叶片28带动滤芯支撑架29沿着第二螺旋滑道一边转动一边向下运动,支撑架29底部的底板40上连接有缓冲部件27,缓冲部件27的另一端固定在集灰腔内壁19上的支撑块20上;支撑架29连同滤芯30旋转向下运动,滤芯30下端进入集灰腔34内,环形集灰腔外壁18内靠近集灰腔34入口端对应设置有刮刀22,刮刀22下方设有毛刷23,毛刷23对面的集灰腔内壁19内对应位置设有喷嘴24用以向滤芯30背面喷吹反吹气体;在刮刀22、毛刷23和喷嘴24的共同作用下去除滤芯30吸附过滤的颗粒物,滤芯30得以再生。A small part of the exhaust gas hits the shunt cover 12 and flows down along the shunt cover 12, and hits 3-10 blades 28 fixed on the upper top plate 39 of the filter element support frame 29. The inner wall of the filter element support frame 29 is provided with a spiral slideway 36, The spiral slideway 36 cooperates with the second spiral slideway on the outer wall of the annular inner baffle plate 15, the exhaust gas hits the blade 28, and the blade 28 drives the filter element support frame 29 to move downward while rotating along the second spiral slideway, and the bottom of the support frame 29 The bottom plate 40 is connected with a buffer component 27, and the other end of the buffer component 27 is fixed on the support block 20 on the inner wall 19 of the ash collection chamber; the support frame 29 rotates and moves downward together with the filter core 30, and the lower end of the filter core 30 enters the ash collection chamber 34, A scraper 22 is arranged on the outer wall 18 of the ring-shaped ash-collecting chamber near the entrance of the ash-collecting chamber 34. A brush 23 is provided below the scraper 22. A nozzle 24 is provided at a corresponding position in the inner wall 19 of the ash-collecting chamber opposite to the brush 23 to feed the filter element. 30 blows back blowing gas; under the joint action of the scraper 22, the brush 23 and the nozzle 24, the particles adsorbed and filtered by the filter element 30 are removed, and the filter element 30 is regenerated.
作为优选,分支入口的数量为4-8个。Preferably, the number of branch entrances is 4-8.
作为优选,喷雾器距离分支入口的距离为1-1.5m。Preferably, the distance between the sprayer and the branch inlet is 1-1.5m.
作为优选,除尘器的滤芯为活性碳滤芯、聚丙烯纤维、金属纤维、玻璃纤维。Preferably, the filter element of the dust remover is an activated carbon filter element, polypropylene fiber, metal fiber, glass fiber.
作为优选,叶片的数量为7片。Preferably, the number of blades is 7 pieces.
作为优选,缓冲部件为阻尼杆、液压杆或者弹簧,其数量可以是2-8个。Preferably, the buffer component is a damping rod, a hydraulic rod or a spring, and the number thereof may be 2-8.
作为优选,分流罩上设有泄流口。Preferably, the shunt cover is provided with a discharge port.
本发明的有益效果是:The beneficial effects of the present invention are:
1、吸收塔布气手段独特,极大的提高了气体分布效果以及气液接触效率,大幅提升了净化效果。1. The method of absorbing tabu gas is unique, which greatly improves the gas distribution effect and gas-liquid contact efficiency, and greatly improves the purification effect.
2、除尘器在工作中滤芯能够不断的旋转运动进行再生循环使用,并且再生操作不需额外的运行动力,仅依靠尾气自身的动能就能实现滤芯的运动,节能低耗。2. During the work of the dust collector, the filter element can rotate continuously for regeneration and recycling, and the regeneration operation does not require additional operating power, and the movement of the filter element can be realized only by the kinetic energy of the exhaust gas itself, saving energy and low consumption.
3、通过将湿法除尘和干法除尘手段相结合,高效的去除电石炉尾气中的固体颗粒物,节能环保。3. Through the combination of wet dust removal and dry dust removal, the solid particles in the exhaust gas of calcium carbide furnace can be efficiently removed, which is energy-saving and environmentally friendly.
附图说明Description of drawings
图1是本发明的工艺路线图。Fig. 1 is a process roadmap of the present invention.
图2是本发明的湿法吸收塔的示意图。Fig. 2 is a schematic diagram of the wet absorption tower of the present invention.
图3是本发明的除尘器的主视图。Fig. 3 is a front view of the dust remover of the present invention.
图4是本发明的除尘器的AA剖视图。Fig. 4 is an AA sectional view of the dust remover of the present invention.
图5是本发明的除尘器的分流罩的示意图。Fig. 5 is a schematic diagram of the shunt hood of the dust remover of the present invention.
图6是本发明的除尘器的支撑架的透视图。Fig. 6 is a perspective view of the support frame of the dust remover of the present invention.
附图标记与其所对应的部件说明如下:The descriptions of the reference signs and their corresponding parts are as follows:
1、吸收塔;2、吸收塔气体入口;3、吸收塔气体出口;4、除雾器;5、喷雾器;6、分支入口;7、循环泵;10、除尘器;11、除尘器入口;12、分流罩;13、泄流口;14、环形外挡板;15、环形内挡板;16、渐扩段;17、扩充段;19、下挡板;20、支撑块;21、密封环;22、刮刀;23、毛刷;24、喷嘴;25、反吹阀;26、卸灰阀;27、缓冲部件;28、叶片;29、支撑架;30、滤芯;31滤板;32、排气腔;33、流动腔;34、集灰腔;35、泄流腔;36、螺旋滑道;38、紧固环;39、顶板;40、底板1. Absorption tower; 2. Absorption tower gas inlet; 3. Absorption tower gas outlet; 4. Demister; 5. Sprayer; 6. Branch inlet; 7. Circulation pump; 10. Dust collector; 11. Dust collector inlet; 12. Shunt cover; 13. Discharge port; 14. Annular outer baffle; 15. Annular inner baffle; 16. Gradually expanding section; 17. Expansion section; 19. Lower baffle; 20. Support block; 21. Seal Ring; 22, scraper; 23, brush; 24, nozzle; 25, blowback valve; 26, ash discharge valve; 27, buffer component; 28, blade; 29, support frame; 30, filter element; 31 filter plate; , exhaust cavity; 33, flow cavity; 34, ash collection cavity; 35, discharge cavity; 36, spiral slideway; 38, fastening ring; 39, top plate; 40, bottom plate
具体实施方式Detailed ways
以下实施例用于对本发明的说明,但不用来限制本发明的范围。The following examples are used to illustrate the present invention, but not to limit the scope of the present invention.
本发明是一种电石炉尾气的净化方法,它包括湿法吸收步骤和干法除尘步骤。从电石炉来的尾气温度约600℃,尾气首先进入吸收塔内,尾气从吸收塔的气体入口进入,与雾化的水接触反应,尾气释放热量降温,水分迅速蒸发;尾气中的颗粒物与雾化水充分接触,离开吸收塔的尾气中的含尘量在40mg/Nm3以下,温度小于45℃。吸收的粉尘随吸收液一同落入吸收塔底部。The invention relates to a method for purifying the tail gas of a calcium carbide furnace, which comprises a wet absorption step and a dry dust removal step. The temperature of the tail gas from the calcium carbide furnace is about 600°C. The tail gas first enters the absorption tower, and the tail gas enters from the gas inlet of the absorption tower, and reacts with the atomized water. The tail gas releases heat to cool down, and the water evaporates rapidly; the particles and fog in the tail gas The chemical water is fully contacted, the dust content in the tail gas leaving the absorption tower is below 40mg/Nm 3 , and the temperature is below 45°C. The absorbed dust falls into the bottom of the absorption tower together with the absorption liquid.
经过吸收塔处理的尾气随后进入除尘器中,经过除尘器的滤芯,有效的去除尾气中剩余的固体颗粒物,由于尾气中的大量粉尘已经在吸收塔中去除,因此,除尘器中的滤芯选择更为精细的级别,进一步去除细微的粉尘。经过净化后的尾气可经引风机等机构排放大气中。The exhaust gas treated by the absorption tower then enters the dust collector, and passes through the filter element of the dust collector to effectively remove the remaining solid particles in the exhaust gas. Since a large amount of dust in the exhaust gas has been removed in the absorption tower, the filter element selection in the dust collector is better. For the fine level, further remove fine dust. The purified exhaust gas can be discharged into the atmosphere through induced draft fan and other mechanisms.
实施例:Example:
如图1、图2所示,电石炉尾气温度约600℃,尾气中含有CO、粉尘等。尾气首先进入吸收塔1,吸收塔气体入口2进入吸收塔1之后变为4个分支入口6,分支入口6从上至下沿斜线均匀分布在吸收塔内,最上方的分支入口距离气体入口2最近,最下方的分支入口距离气体入口2最远。4个分支入口基本能够实现气体的均匀分布。在各个分支入口的上部均设有一对应的喷雾器5,喷雾器5距离分支入口1m。由于气体入口分成若干个分支入口,这样即可以通过在各分支入口处设置对应喷雾器以提高捕捉效率,又可以提高尾气在吸收塔内的分布程度。除了对应设置的喷雾器5,在吸收塔的顶部同样设置有常规的喷雾器,以进一步提高气液接触效率。雾化水充分捕捉粉尘后落入吸收塔底部,底部的吸收液在循环泵7的作用下循环回喷雾器继续参与吸收。通过这种强烈的传质过程,尾气中的大部分粉尘得以充分的去除。在吸收塔的顶端设有除雾器4,含湿尾气经过除雾器4后从吸收塔气体出口3排出吸收塔。通过吸收塔后的尾气中,粉尘去除率可达到90%以上,尾气的温度降至60℃以下。As shown in Figure 1 and Figure 2, the temperature of the tail gas of the calcium carbide furnace is about 600°C, and the tail gas contains CO, dust, etc. The exhaust gas first enters the absorption tower 1, and after the gas inlet 2 of the absorption tower enters the absorption tower 1, it becomes four branch inlets 6. The branch inlets 6 are evenly distributed in the absorption tower along the oblique line from top to bottom, and the uppermost branch inlet is far from the gas inlet. 2 is the closest, and the lowermost branch inlet is farthest from the gas inlet 2. The 4 branch inlets can basically realize the uniform distribution of gas. A corresponding sprayer 5 is provided on the upper part of each branch entrance, and the sprayer 5 is 1m away from the branch entrance. Since the gas inlet is divided into several branch inlets, the capture efficiency can be improved by setting corresponding sprayers at each branch inlet, and the distribution degree of the tail gas in the absorption tower can be improved. In addition to the sprayer 5 provided correspondingly, a conventional sprayer is also arranged on the top of the absorption tower to further improve the gas-liquid contact efficiency. After the atomized water fully captures the dust, it falls into the bottom of the absorption tower, and the absorption liquid at the bottom is circulated back to the sprayer under the action of the circulation pump 7 to continue to participate in the absorption. Through this strong mass transfer process, most of the dust in the exhaust gas can be fully removed. A mist eliminator 4 is installed on the top of the absorption tower, and the wet exhaust gas passes through the mist eliminator 4 and is discharged from the absorption tower gas outlet 3. In the tail gas after passing through the absorption tower, the dust removal rate can reach more than 90%, and the temperature of the tail gas drops below 60°C.
从吸收塔1排出的尾气随后进入除尘器10内,尾气首先从除尘器入口11进入除尘器,尾气首先正面冲击在分流罩12上,分流罩为圆锥形体,在分流罩12的作用下,大部分尾气经过渐扩段进入除尘器扩充段内的流动腔33,除尘器的扩充段器壁同内部的环形外挡板14构成了流动腔33,尾气经过流动腔33之后同滤芯支撑架29内的滤芯30接触,滤芯30为玻璃纤维滤芯。环形外挡板14连同环形内挡板15与集灰腔外壁18和集灰腔内壁19共同构成了滤芯30上的气体流动通路,滤芯30与集灰腔外壁18之间设有密封环21,用以防止气体未经滤芯30而进入集灰腔34。气体中的颗粒物被滤芯30吸附过滤,净化后的气体经过滤芯30过滤后进入排气腔32排出除尘器。环形的滤芯30在过滤期间会在滤芯的表面沉积一层过滤的颗粒物,沉积的颗粒物会降低滤芯的过滤效果,因此滤芯需要定期的再生。The tail gas discharged from the absorption tower 1 then enters the dust collector 10. The tail gas first enters the dust collector from the dust collector inlet 11, and the tail gas first impacts on the shunt cover 12 head-on. The shunt cover is a conical body. Part of the exhaust gas enters the flow chamber 33 in the expansion section of the dust collector through the gradual expansion section. The wall of the expansion section of the dust collector and the inner annular outer baffle 14 constitute the flow chamber 33. Contact with the filter element 30, the filter element 30 is a glass fiber filter element. The annular outer baffle plate 14 together with the annular inner baffle plate 15, the outer wall 18 of the ash collection chamber and the inner wall 19 of the ash collection chamber together constitute the gas flow path on the filter element 30, and a sealing ring 21 is arranged between the filter element 30 and the outer wall 18 of the ash collection chamber. It is used to prevent gas from entering the ash collection chamber 34 without passing through the filter element 30 . Particles in the gas are adsorbed and filtered by the filter element 30, and the purified gas enters the exhaust chamber 32 and is discharged from the dust collector after being filtered by the filter element 30. The ring-shaped filter element 30 will deposit a layer of filtered particles on the surface of the filter element during filtering, and the deposited particles will reduce the filtering effect of the filter element, so the filter element needs to be periodically regenerated.
滤芯30的再生过程:参见图3、图4、图6。尾气从除尘器入口11进入除尘器后,如前所述,大部分的尾气在分流罩12引导下进入了流动腔33内进入过滤阶段,此外,有一小部分尾气撞击分流罩12之后沿着分流罩12向下流动,撞击到滤芯支撑架29上部顶板39上固定的叶片28,滤芯支撑架29内壁上设有螺旋滑道36,螺旋滑道36与环形内挡板外壁的螺旋滑道(未示出)配合,因此,尾气撞击叶片28,叶片28带动滤芯支撑架29在螺旋滑道的支撑和引导下一边转动一边向下运动。支撑架29连同滤芯30旋转向下运动,进入集灰腔34内,支撑架29与集灰腔内壁19紧密接触,滤芯30与集灰腔外壁18留有一定空间,环形集灰腔外壁18内靠近集灰腔入口端首先对应设置有两片刮刀22,刮刀22贴近滤芯30,刮刀22下方设有毛刷23,毛刷23的刷毛接触滤芯30,毛刷23对面的集灰腔内壁19内对应位置设有喷嘴24用以向滤芯30背面喷吹反吹气体,反吹阀25控制反吹气体的流量。在刮刀22的作用下,旋转的滤芯30表面沉积的杂质被刮刀刮除,滤芯30进一步旋转下降,随后在毛刷23和喷嘴24的共同作用下进一步去除滤芯30吸附过滤的颗粒物,滤芯30在多重再生手段处理下得以再生。被脱除的杂质落入集灰腔34底部,积累到一定程度后通过卸灰阀26排出除尘器外。集灰腔34内部积灰的量可以通过颗粒传感器探测等自动探测手段探测。The regeneration process of the filter element 30: see Fig. 3, Fig. 4, Fig. 6. After the exhaust gas enters the dust collector from the dust collector inlet 11, as mentioned above, most of the exhaust gas enters the flow chamber 33 under the guidance of the shunt cover 12 and enters the filtering stage. The cover 12 flows downwards and hits the fixed blade 28 on the top plate 39 of the filter element support frame 29. The inner wall of the filter element support frame 29 is provided with a spiral slideway 36, and the spiral slideway 36 and the spiral slideway on the outer wall of the annular inner baffle (not shown) Shown) fits, therefore, tail gas hits vane 28, and vane 28 drives filter element support frame 29 to move downwards while rotating under the support and guidance of the spiral slideway. The support frame 29 rotates and moves downward together with the filter element 30 and enters the ash collection chamber 34. The support frame 29 is in close contact with the inner wall 19 of the ash collection chamber. There is a certain space between the filter element 30 and the outer wall 18 of the ash collection chamber. Close to the entrance of the ash collection chamber, there are two scrapers 22 correspondingly arranged first. The scrapers 22 are close to the filter element 30. A brush 23 is arranged under the scraper 22. The bristles of the brush 23 contact the filter element 30. The inner wall 19 of the ash collection chamber opposite to the brush 23 is A nozzle 24 is provided at a corresponding position for blowing back blowing gas to the back of the filter element 30 , and a back blowing valve 25 controls the flow rate of the back blowing gas. Under the action of the scraper 22, the impurities deposited on the surface of the rotating filter element 30 are scraped off by the scraper, and the filter element 30 further rotates and descends, and then the particulate matter adsorbed and filtered by the filter element 30 is further removed under the combined action of the brush 23 and the nozzle 24. It can be regenerated under the treatment of multiple regeneration methods. The removed impurities fall into the bottom of the ash collecting chamber 34, and after accumulating to a certain extent, they are discharged out of the dust collector through the ash unloading valve 26. The amount of ash accumulated in the ash collection chamber 34 can be detected by automatic detection means such as particle sensor detection.
参见图3,分流罩12的底部圆周同环形内挡板15固定连接,支撑架29绕着环形内挡板15转动下降,支撑架29底部的底板40上连接有缓冲部件27,缓冲部件优选为阻尼杆,缓冲部件27的另一端固定在集灰腔内壁上的支撑块20上。缓冲部件27的作用是控制支撑架29的下降速度,防止下降过快。缓冲部件27的位置和数量可以根据需要进行选择,当然以不阻挡喷嘴24为宜,图3中仅是为了表明缓冲部件27的存在,而并非限定缓冲部件27和喷嘴24的相对位置。当然,也可以采用其他具有类似功能的装置,例如液压杆、弹簧等。此外,支撑架29的下降速度也可以通过设置不同数量以及角度的叶片28进行调节,本实施例中叶片的数量优选为7片,根据尾气的流速,7片叶片可以实现较好的旋转速度,也可以通过设置更少或更多的叶片以降低或增加支撑架29的下降速度,例如可以是3片、5片、10片等。再生过程中,当滤芯30的大部分已经下降入集灰腔34并被再生之后,可以控制缓冲部件或其它类似部件反向对支撑架29施压,例如停止进气,则压缩的缓冲部件会促使支撑架29反向旋转上升回到初始的工作状态,依此循环往复工作。Referring to Fig. 3, the bottom circumference of the shunt cover 12 is fixedly connected with the annular inner baffle 15, the support frame 29 rotates and descends around the annular inner baffle 15, and the bottom plate 40 at the bottom of the support frame 29 is connected with a buffer member 27, the buffer member is preferably The damping rod, the other end of the buffer component 27 is fixed on the support block 20 on the inner wall of the ash collecting cavity. The effect of buffer member 27 is to control the descending speed of support frame 29, prevents descending too fast. The position and quantity of the buffering member 27 can be selected according to needs, and it is advisable not to block the nozzle 24 of course. In FIG. Of course, other devices with similar functions can also be used, such as hydraulic rods, springs and the like. In addition, the descending speed of the support frame 29 can also be adjusted by setting blades 28 of different numbers and angles. In this embodiment, the number of blades is preferably 7. According to the flow velocity of the exhaust gas, 7 blades can achieve a better rotation speed. It is also possible to reduce or increase the descending speed of the support frame 29 by setting fewer or more blades, for example, 3 blades, 5 blades, 10 blades, etc. During the regeneration process, when most of the filter element 30 has fallen into the ash collection chamber 34 and is regenerated, the buffer component or other similar components can be controlled to reversely pressurize the support frame 29, such as stopping the air intake, the compressed buffer component will Prompt the support frame 29 to reversely rotate and rise back to the initial working state, and thus work in a cyclical manner.
参见图5,该图为分流罩12的立体图,分流罩12上可以设置泄流口13,正常情况下泄流口13封闭,气体不能从分流罩12通过。当除尘器内的压力传感器(未示出)测量到除尘器内压力高于正常值后,泄流口13打开,气流可以从泄流口13流过,进入泄流腔35,经过滤板31过滤后排出除尘器。泄流口13的打开和闭合可以通过泄流口处的闭合开关远程控制。除尘器运行时,有时会遇到流量、流速波动较大的输入气流,有时会遇到过滤器的意外堵塞,当遇到类似的使除尘器内压力增高的情况时,为保证生产安全可以打开泄流口13以迅速降低除尘器内的压力,防止滤芯或除尘器的损坏,由于过滤板31的存在,也可以保证泄流气体的安全性。Referring to FIG. 5 , this figure is a perspective view of the shunt cover 12 . A discharge port 13 may be provided on the flow cover 12 . Normally, the discharge port 13 is closed and gas cannot pass through the flow cover 12 . When the pressure sensor (not shown) in the dust collector measures that the pressure in the dust collector is higher than the normal value, the discharge port 13 is opened, and the air flow can flow through the discharge port 13, enter the discharge cavity 35, and pass through the filter plate 31 After filtration, it is discharged from the dust collector. The opening and closing of the discharge port 13 can be remotely controlled by a closing switch at the discharge port. When the dust collector is running, sometimes it encounters the input air flow with large fluctuations in flow rate and flow velocity, and sometimes encounters accidental clogging of the filter. When encountering a similar situation that increases the pressure inside the dust collector, it can be opened to ensure production safety. The discharge port 13 is used to quickly reduce the pressure in the dust collector to prevent damage to the filter element or the dust collector. Due to the existence of the filter plate 31, the safety of the discharged gas can also be ensured.
参见图6,该图为支撑架29的立体图,支撑架29上端的顶板39上固定有叶片28,支撑架29的主体由竖直的格栅以及起到加固作用的多个紧固环38构成大致网状的透气结构,支撑架29的内壁固定设有螺旋滑道36以引导支撑架29围绕环形内挡板旋转下降。支撑架29以及螺旋滑道36的材料可以是任意的具有一定刚性的材料,例如不锈钢、塑料等。Referring to Fig. 6, this figure is a perspective view of the support frame 29, the blade 28 is fixed on the top plate 39 at the upper end of the support frame 29, the main body of the support frame 29 is composed of a vertical grid and a plurality of fastening rings 38 for reinforcement The substantially net-like air-permeable structure, the inner wall of the support frame 29 is fixed with a spiral slideway 36 to guide the support frame 29 to rotate and descend around the annular inner baffle. The material of the support frame 29 and the spiral slideway 36 can be any material with certain rigidity, such as stainless steel, plastic and the like.
尾气经过吸收塔1、除尘器10之后,气体中的固体颗粒物基本都被去除,气体达到排放标准。After the tail gas passes through the absorption tower 1 and the dust collector 10, the solid particles in the gas are basically removed, and the gas reaches the discharge standard.
本发明的净化方法中,所使用的吸收塔通过独特的布气手段,极大的提高了气体分布效果以及气液接触效率,大幅提升了净化效果。所使用的除尘器在工作中滤芯能够不断的进行再生循环使用,并且不需额外的运行动力,仅依靠尾气自身的动能就能实现滤芯的再生。由于本发明的吸收塔和除尘器的共同联用,有效的去除了电石炉尾气中的有害物质,实现了尾气的清洁排放。In the purification method of the present invention, the absorption tower used greatly improves the gas distribution effect and gas-liquid contact efficiency through a unique gas distribution means, and greatly improves the purification effect. The filter element used by the dust collector can be continuously regenerated and recycled during operation, and no additional operating power is required, and the regeneration of the filter element can be realized only by the kinetic energy of the exhaust gas itself. Due to the combined use of the absorption tower and the dust collector of the present invention, the harmful substances in the tail gas of the calcium carbide furnace are effectively removed, and the clean discharge of the tail gas is realized.
以上所述的实施例只是本发明的一种较佳的方案,并非对本发明作任何形式上的限制,在不超出权利要求所记载的技术方案的前提下还有其它的变体及改型。The embodiment described above is only a preferred solution of the present invention, and does not limit the present invention in any form. There are other variations and modifications on the premise of not exceeding the technical solution described in the claims.
Claims (7)
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CN109862954A (en) * | 2016-10-18 | 2019-06-07 | 虎格工程股份公司 | Carbon black granules filter and method for running carbon black granules filter |
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CN103708432A (en) * | 2013-12-27 | 2014-04-09 | 成都易态科技有限公司 | Method and equipment for recovering yellow phosphorus from electric furnace phosphorus-producing furnace gas and special phosphorus collecting device |
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GB1112309A (en) * | 1964-09-29 | 1968-05-01 | Max Berz | Improved process and apparatus for the separation of solid particles from fluids |
CN201551929U (en) * | 2009-11-26 | 2010-08-18 | 北京有色金属研究总院 | Tail gas self-purifying filter device for straight-pulling silicon single-crystal furnace |
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