CN204816206U - Coke oven flue desulphurization of exhaust gas denitration integrated device - Google Patents
Coke oven flue desulphurization of exhaust gas denitration integrated device Download PDFInfo
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Abstract
本实用新型公开了一种焦炉烟道废气脱硫脱硝一体化装置,在反应塔的侧部设有烟气入口,反应塔内在所述烟气入口的上方依次设有脱硫区、脱硝区、除雾区,反应塔的顶部设有烟气出口;反应塔内位于烟气入口的下方设为浆液池。脱硫区设有数个脱硫喷淋头、数个所述脱硫喷淋头并列连接在第一循环管道上;所述脱硝区设有数个脱硝喷淋头、数个所述脱硝喷淋头并列连接在第二循环管道上;所述第一循环管道、第二循环管道与所述浆液池和/或溶液池连通。本实用新型具有投资少,能耗低,系统简单可靠、运行成本低、现场资源利用率高、脱硫脱硝效率高,脱硫效率在95%以上,脱硝效率在80%以上,经处理后的烟气完全符合国家炼焦化学工业污染物排放标准。
The utility model discloses an integrated device for desulfurization and denitrification of coke oven flue waste gas. A flue gas inlet is arranged on the side of a reaction tower, and a desulfurization area, a denitrification area, a denitrification area, and a In the fog zone, the top of the reaction tower is provided with a flue gas outlet; the reaction tower is located below the flue gas inlet as a slurry pool. The desulfurization area is provided with several desulfurization spray heads, and several desulfurization spray heads are connected in parallel on the first circulation pipeline; On the second circulation pipeline; the first circulation pipeline and the second circulation pipeline communicate with the slurry pool and/or the solution pool. The utility model has the advantages of low investment, low energy consumption, simple and reliable system, low operating cost, high utilization rate of on-site resources, high desulfurization and denitrification efficiency, desulfurization efficiency of more than 95%, and denitrification efficiency of more than 80%. It fully complies with the national coking chemical industry pollutant discharge standard.
Description
技术领域:Technical field:
本实用新型涉及一种焦炉烟道废气脱硫脱硝一体化装置,属于焦化废气处理技术领域。The utility model relates to an integrated device for desulfurization and denitrification of coke oven flue waste gas, which belongs to the technical field of coking waste gas treatment.
背景技术:Background technique:
焦炭是煤炭转化的一个主要附产品,主要用于高炉炼铁,起还原剂、发热剂和料柱骨架作用,是钢铁工业重要的原料。Coke is a major by-product of coal conversion. It is mainly used in blast furnace ironmaking. It acts as a reducing agent, exothermic agent and material column skeleton. It is an important raw material for the iron and steel industry.
焦炭是煤在炼焦炉碳化室中在隔绝空气的条件下进行加热,经过一系列物理变化和化学反应的复杂过程形成的。在焦炭干馏过程中产生的焦炉煤气含有二氧化硫与氮氧化物等污染物,在后续使用过程中会产生新的污染。这些二氧化硫与氮氧化物是PM2.5颗粒物的重要组成成份,也是形成酸雨、雾霾等的主要原因。它的产生机理是:碳化室的热源是由一定比例的焦炉煤气和高炉煤气加热立火道所提供,对加热煤气所产生的废气称为炼焦炉废气;而煤气中含有一定量的H2S等硫化物,燃烧后生成SO2,煤气与空气在焦炉立火道燃烧时,生成氮氧化物NOx(有温度热力型、碳氢燃料快速型和含氮组分燃料型三种)。目前,我国炼焦炉废气的二氧化硫和氮氧化物没有采取减排措施,根据环保部门检测,国内现有焦炉所排放的SO2和NOx的浓度大多不能满足国家最新出台的《炼焦化学工业污染物排放标准》。且新《标准》在2015年1月1日起,对SO2和NOx的排放浓度要求更高。因此,炼焦炉脱硫脱硝改造是治理大气污染一项紧迫的任务,对炼焦炉废气脱硫脱硝技术的研究,具有极其深远的意义。Coke is formed by heating coal in the carbonization chamber of a coke oven under air-isolated conditions and undergoing a series of complex processes of physical changes and chemical reactions. The coke oven gas produced during coke carbonization contains pollutants such as sulfur dioxide and nitrogen oxides, which will generate new pollution in the subsequent use process. These sulfur dioxide and nitrogen oxides are important components of PM2.5 particulate matter, and are also the main cause of acid rain and smog. Its production mechanism is: the heat source of the carbonization chamber is provided by a certain proportion of coke oven gas and blast furnace gas heating the vertical fire channel, and the waste gas produced by heating the gas is called coke oven waste gas; and the gas contains a certain amount of H 2 S and other sulfides generate SO 2 after combustion, and nitrogen oxides NOx are generated when gas and air are burned in the vertical flue of the coke oven (there are three kinds of temperature thermal type, hydrocarbon fuel fast type and nitrogen-containing component fuel type). At present, no measures have been taken to reduce the emission of sulfur dioxide and nitrogen oxides in coke oven exhaust gas in China. According to the detection of the environmental protection department, most of the concentrations of SO 2 and NOx emitted by domestic coke ovens cannot meet the latest "Coking Chemical Industry Pollutants" issued by the country. Emission Standards". And the new "Standard" has higher requirements on the emission concentration of SO 2 and NOx starting from January 1, 2015. Therefore, the transformation of desulfurization and denitrification of coke oven is an urgent task to control air pollution, and the research on desulfurization and denitrification technology of coke oven exhaust gas has extremely far-reaching significance.
发明内容:Invention content:
为克服现有技术的缺陷,本实用新型的目的在于提供一种焦炉烟道废气脱硫脱硝一体化装置,重点解决适合我国炼焦炉工艺特点及烟道废气特性的二氧化硫和氮氧化物达标排放技术,开发一种焦炉烟道废气脱硫脱硝一体化装置。采用该装置能够有效地提高烟气的脱硫、脱硝效率和脱硫脱硝吸收剂的利用率,并且该装置相比火电厂常用的SCR/SNCR脱硝装置造价成本低廉,碱性吸收液可用廉价的钙碱再生,脱硫副产物石膏及脱硝副产物硝酸盐可回收。In order to overcome the defects of the existing technology, the purpose of this utility model is to provide an integrated device for desulfurization and denitrification of coke oven flue gas, focusing on solving the technology of sulfur dioxide and nitrogen oxide emission standards suitable for the characteristics of my country's coke oven process and flue gas characteristics , to develop an integrated device for coke oven flue gas desulfurization and denitrification. The device can effectively improve the desulfurization and denitrification efficiency of flue gas and the utilization rate of desulfurization and denitrification absorbent, and the cost of the device is lower than that of SCR/SNCR denitrification devices commonly used in thermal power plants, and the alkaline absorption liquid can be made of cheap calcium alkali Regeneration, desulfurization by-product gypsum and denitrification by-product nitrate can be recovered.
本实用新型解决技术问题采用如下技术方案:The utility model solves the technical problem and adopts the following technical solutions:
一种焦炉烟道废气脱硫脱硝一体化装置,在反应塔的侧部设有烟气入口,所述反应塔内在所述烟气入口的上方依次设有脱硫区、脱硝区、除雾区,反应塔的顶部设有烟气出口;反应塔内位于烟气入口的下方设为浆液池。An integrated device for desulfurization and denitrification of coke oven flue exhaust gas, a flue gas inlet is provided on the side of the reaction tower, and a desulfurization area, a denitrification area, and a demisting area are sequentially arranged in the reaction tower above the flue gas inlet, The top of the reaction tower is provided with a flue gas outlet; the inside of the reaction tower is set as a slurry pool below the flue gas inlet.
所述脱硫区设有数个脱硫喷淋头、数个所述脱硫喷淋头并列连接在第一循环管道上;所述脱硝区设有数个脱硝喷淋头、数个所述脱硝喷淋头并列连接在第二循环管道上;所述第一循环管道、第二循环管道与所述浆液池和/或溶液池连通。The desulfurization area is provided with several desulfurization spray heads, and several desulfurization spray heads are connected in parallel on the first circulation pipeline; Connected to the second circulation pipeline; the first circulation pipeline and the second circulation pipeline communicate with the slurry pool and/or the solution pool.
在所述脱硝喷淋头的下方设有数个臭氧喷头,各所述臭氧喷头经臭氧输送管道与臭氧制备装置连通。Several ozone shower heads are arranged below the denitrification shower head, and each ozone shower head communicates with the ozone preparation device through an ozone delivery pipeline.
所述除雾区设有数个水雾喷头,数个所述水雾喷头在喷淋水管道上间隔交错排布,所述喷淋水管道与冲洗水箱连通,并在管道上设有冲洗泵。The demisting area is provided with several water mist nozzles, and the several water mist nozzles are alternately arranged on the spray water pipeline, and the spray water pipeline is connected with the flushing water tank, and a flushing pump is provided on the pipeline.
所述浆液池经输送管道与吸收液制备装置连通,并在所述输送管道上设置有给液泵。The slurry pool communicates with the absorption liquid preparation device through a delivery pipeline, and a feed pump is arranged on the delivery pipeline.
所述溶液池连通过渡池、所述过渡池连通再生池,所述再生池分别连通碱性溶液制备系统和浆液池,并且,所述再生池与副产物回收处理系统通过管道形成一个闭路循环,并在管道上设置有渣浆泵将再生池中的浆液泵送至所述副产物回收处理系统。The solution pool is connected to the transition pool, the transition pool is connected to the regeneration pool, and the regeneration pool is respectively connected to the alkaline solution preparation system and the slurry pool, and the regeneration pool and the by-product recovery treatment system form a closed loop through pipelines, A slurry pump is provided on the pipeline to pump the slurry in the regeneration tank to the by-product recovery treatment system.
在所述烟气出口设有引风机。An induced draft fan is provided at the flue gas outlet.
与已有技术相比,本实用新型的有益效果体现在:Compared with the prior art, the beneficial effects of the utility model are reflected in:
本实用新型具有投资少,能耗低,系统简单可靠、运行成本低、现场资源利用率高、脱硫脱硝效率高,脱硫效率在95%以上,脱硝效率在80%以上,经处理后的烟气完全符合国家炼焦化学工业污染物排放标准。The utility model has the advantages of low investment, low energy consumption, simple and reliable system, low operating cost, high utilization rate of on-site resources, high desulfurization and denitrification efficiency, desulfurization efficiency of more than 95%, and denitrification efficiency of more than 80%. It fully complies with the national coking chemical industry pollutant discharge standard.
本实用新型是基于氧化吸收的原理,是一种新的烟气脱除NOx和SO2的方法,该法旨在向烟气或废气中添加一定量的臭氧,利用臭氧的氧化作用调节烟气中的NO2含量达到NOx总量的50%,使之与NO合成易溶于碱液的N2O3,再利用碱性吸收液将二氧化硫和氮氧化物吸收。产生的反应液与Ca(OH)2反应再生成的碱性吸收液循环利用,氧化后副产物硝酸盐及石膏分别回收。该装置脱硫效率在95%以上,脱硝效率在80%以上。The utility model is based on the principle of oxidation absorption, and is a new method for removing NOx and SO2 from flue gas. The NO 2 content of the NOx reaches 50% of the total NOx, so that it can be combined with NO to form N 2 O 3 , which is easily soluble in alkali solution, and then the sulfur dioxide and nitrogen oxides can be absorbed by the alkaline absorption solution. The resulting reaction liquid reacts with Ca(OH) 2 to regenerate the alkaline absorption liquid for recycling, and the oxidized by-products nitrate and gypsum are recovered separately. The desulfurization efficiency of the device is above 95%, and the denitrification efficiency is above 80%.
附图说明:Description of drawings:
图1为本实用新型的结构示意图。Fig. 1 is the structural representation of the utility model.
图中标号:1反应塔,2副产物回收处理系统,3臭氧制备装置,4烟气入口,5除雾区,6脱硝区,7脱硫区,8浆液池,9循环泵,10第一循环管道,11脱硫喷淋头,12脱硝喷淋头,13给液泵,14吸收液制备装置,15再生池,16烟气出口,17引风机,18过渡池,19溶液池,20渣浆泵,21碱性溶液制备系统,22冲洗水箱,23冲洗泵,24第二循环管道。Labels in the figure: 1 reaction tower, 2 by-product recovery and treatment system, 3 ozone preparation device, 4 flue gas inlet, 5 defogging area, 6 denitrification area, 7 desulfurization area, 8 slurry tank, 9 circulation pump, 10 first cycle Pipeline, 11 desulfurization spray head, 12 denitrification spray head, 13 liquid feed pump, 14 absorption liquid preparation device, 15 regeneration tank, 16 flue gas outlet, 17 induced draft fan, 18 transition tank, 19 solution tank, 20 slurry pump , 21 alkaline solution preparation system, 22 flushing water tank, 23 flushing pump, 24 second circulation pipeline.
以下通过具体实施方式,并结合附图对本实用新型作进一步说明。The utility model will be further described below through specific embodiments in conjunction with the accompanying drawings.
具体实施方式:Detailed ways:
实施例:本实施例装置是在反应塔1的侧部设有烟气入口4,反应塔1内在烟气入口4的上方依次设有脱硫区7、脱硝区6、除雾区5,反应塔的顶部设有烟气出口16;反应塔内位于烟气入口4的下方设为浆液池8。Embodiment: The device of this embodiment is provided with a flue gas inlet 4 on the side of the reaction tower 1, and the reaction tower 1 is provided with a desulfurization zone 7, a denitrification zone 6, and a demisting zone 5 successively above the flue gas inlet 4. The reaction tower A flue gas outlet 16 is provided at the top of the reactor; a slurry pool 8 is located below the flue gas inlet 4 in the reaction tower.
脱硫区7设有数个脱硫喷淋头11、数个脱硫喷淋头并列连接在第一循环管道10上;脱硝区6设有数个脱硝喷淋头12、并且数个脱硝喷淋头并列连接在第二循环管道24上;该第一循环管道、第二循环管道与浆液池和/或溶液池19连通。The desulfurization zone 7 is provided with several desulfurization spray heads 11, and several desulfurization spray heads are connected in parallel on the first circulation pipeline 10; On the second circulation pipeline 24 ; the first circulation pipeline and the second circulation pipeline communicate with the slurry pool and/or the solution pool 19 .
在脱硝喷淋头12的下方设有数个臭氧喷头,各臭氧喷头经臭氧输送管道与臭氧制备装置3连通。除雾区5同样设有数个水雾喷头,该数个水雾喷头在喷淋水管道上间隔交错排布,喷淋水管道与冲洗水箱22连通,并在管道上设有冲洗泵23。Several ozone shower heads are arranged below the denitrification shower head 12, and each ozone shower head communicates with the ozone preparation device 3 through an ozone delivery pipeline. The demister area 5 is also provided with several water mist nozzles, which are alternately arranged at intervals on the spray water pipeline, and the spray water pipeline is connected with the flush water tank 22, and a flush pump 23 is provided on the pipeline.
浆液池8经输送管道与吸收液制备装置14连通,并在输送管道上设置有给液泵13。The slurry pool 8 communicates with the absorption liquid preparation device 14 through the delivery pipeline, and a feed pump 13 is arranged on the delivery pipeline.
溶液池19连通过渡池18、过渡池连通再生池15,再生池15分别连通碱性溶液制备系统21和浆液池8,并且,再生池15与副产物回收处理系统2通过管道形成一个闭路循环,并在管道上设置有渣浆泵20将再生池15中的浆液泵送至副产物回收处理系统2。The solution pool 19 is connected to the transition pool 18, and the transition pool is connected to the regeneration pool 15, and the regeneration pool 15 is connected to the alkaline solution preparation system 21 and the slurry pool 8 respectively, and the regeneration pool 15 and the by-product recovery treatment system 2 form a closed loop through pipelines, And a slurry pump 20 is provided on the pipeline to pump the slurry in the regeneration tank 15 to the by-product recovery treatment system 2 .
工作原理及工作过程如下:The working principle and working process are as follows:
焦炉烟道废气从烟气入口4进入脱硫脱硝反应塔1,烟气经过脱硫区7的脱硫喷淋头11喷淋的碱性吸收液洗涤后进入脱硝区6,同时空气进入臭氧制备装置3,制备出的O3通过管道进入脱硝区6与烟气混合,使烟气中的NO2占NOX总体积的50%左右,后与脱硝喷淋头12喷淋的碱性吸收液进行反应脱除NOX。反应后的清洁气体经过除雾区5除雾后到烟气出口16,经引风机17进入烟囱排向大气。The coke oven flue gas enters the desulfurization and denitrification reaction tower 1 from the flue gas inlet 4, and the flue gas enters the denitrification area 6 after being washed by the alkaline absorption liquid sprayed by the desulfurization spray head 11 in the desulfurization area 7, and at the same time, the air enters the ozone preparation device 3 , the prepared O3 enters the denitrification zone 6 through the pipeline and mixes with the flue gas, so that the NO2 in the flue gas accounts for about 50% of the total volume of NOx , and then reacts with the alkaline absorption liquid sprayed by the denitrification spray head 12 Remove NOx . The reacted clean gas passes through the demisting zone 5 and goes to the flue gas outlet 16, then enters the chimney through the induced draft fan 17 and is discharged to the atmosphere.
其中脱硫区6及脱硝区7所需的碱性吸收液由循环泵9供给,第一循环管道10、第二循环管道24上各自设有循环泵,两个循环管道连往反应塔1的浆液池8及储存再生后的碱性吸收液的溶液池19;除雾区5主要包括冲洗泵23、冲洗水箱22等。Among them, the alkaline absorption liquid required by the desulfurization zone 6 and the denitrification zone 7 is supplied by the circulation pump 9, and the first circulation pipeline 10 and the second circulation pipeline 24 are respectively equipped with circulation pumps, and the two circulation pipelines are connected to the slurry of the reaction tower 1. The pool 8 and the solution pool 19 for storing the regenerated alkaline absorption liquid; the demisting area 5 mainly includes a flushing pump 23, a flushing water tank 22, and the like.
浆液池8中的循环碱性吸收液由吸收液制备装置14通过给液泵13进行少量适当补充。浆液池8底部浆液达到设定PH值后排入再生池15,与氢氧化钙溶液制备系统21加入的氢氧化钙溶液反应再生成的碱性吸收液通过循环泵9泵入吸收系统循环利用。再生反应后的浆液通过渣浆泵20泵入副产物回收处理系统2进行氧化回收得硫酸钙及硝酸盐。The circulating alkaline absorption liquid in the slurry tank 8 is properly replenished in a small amount by the absorption liquid preparation device 14 through the feed liquid pump 13 . The slurry at the bottom of the slurry tank 8 reaches the set pH value and is discharged into the regeneration tank 15, and the alkaline absorption solution regenerated by reacting with the calcium hydroxide solution added by the calcium hydroxide solution preparation system 21 is pumped into the absorption system by the circulation pump 9 for recycling. The slurry after the regeneration reaction is pumped into the by-product recovery treatment system 2 through the slurry pump 20 to be oxidized and recovered to obtain calcium sulfate and nitrate.
副产物石膏、硝酸盐可作为产品销售,系统结构简单占地面积小,且具有较高的可靠性,系统可用率可达98%以上;无二次污染。The by-products gypsum and nitrate can be sold as products. The system structure is simple and occupies a small area, and has high reliability. The system availability rate can reach more than 98%; there is no secondary pollution.
本装置采用臭氧及碱液脱硝、双碱法脱硫工艺;吸收液再生系统使用但不限于廉价的Ca(OH)2作再生反应剂;吸收系统使用但不限于NaOH作吸收液进行脱硫脱硝。The device adopts ozone and lye denitrification and double alkali desulfurization process; the absorption liquid regeneration system uses but not limited to cheap Ca(OH) 2 as the regeneration reagent; the absorption system uses but not limited to NaOH as the absorption liquid for desulfurization and denitrification.
所述NO2气体采用O3氧化生产工艺,反应生成的NO2占NOx总体积的50%;焦炉烟道废气进入反应塔后,首先在脱硫区与碱性吸收液反应生成亚硫酸盐、硫酸盐和少量亚硝酸盐、硝酸盐,再经过脱硝区与O3混合,使部分NO反应生产NO2。混合气体在脱硝区内被碱性吸收液吸收,生成亚硝酸盐及部分硝酸盐。碱性吸收液吸收二氧化硫及氮氧化物后流入浆液池,当浆液池的PH值达到设定值后将混合溶液排入再生池用Ca(OH)2再生,再生成的碱性吸收液由循环泵泵入吸收系统循环利用,再生反应后的浆液通过渣浆泵泵入副产物回收处理系统。处理后的洁净烟气经除雾区除雾后通过引风机从烟囱排向大气,本装置可设置多层喷淋反应区。 The NO2 gas adopts the O3 oxidation production process, and the NO2 produced by the reaction accounts for 50% of the total volume of NOx ; after the coke oven flue gas enters the reaction tower, it first reacts with the alkaline absorption liquid in the desulfurization zone to form sulfite, Sulfate, a small amount of nitrite, and nitrate are mixed with O 3 through the denitrification zone to make part of NO react to produce NO 2 . The mixed gas is absorbed by the alkaline absorption liquid in the denitrification zone to generate nitrite and part of nitrate. The alkaline absorption liquid absorbs sulfur dioxide and nitrogen oxides and then flows into the slurry pool. When the pH value of the slurry pool reaches the set value, the mixed solution is discharged into the regeneration pool and regenerated with Ca(OH) 2. The regenerated alkaline absorption liquid is circulated The pump is pumped into the absorption system for recycling, and the slurry after the regeneration reaction is pumped into the by-product recovery and treatment system through the slurry pump. The treated clean flue gas is demisted by the demisting area and then discharged from the chimney to the atmosphere through the induced draft fan. The device can be equipped with a multi-layer spray reaction area.
采用上述方法,焦炉烟道废气中二氧化硫、氮氧化物的脱除过程如下:(此处仅以用氢氧化钠作为碱性吸收液时举例)Adopt above-mentioned method, the removal process of sulfur dioxide, nitrogen oxides in coke oven flue gas is as follows: (here only with sodium hydroxide as the example when alkaline absorption liquid)
NO+O3→NO2+O2 NO+O 3 →NO 2 +O 2
2NaOH+SO2→Na2SO3+H2O2NaOH+SO 2 →Na 2 SO 3 +H 2 O
2Na2SO3+O2→2Na2SO4 2Na 2 SO 3 +O 2 →2Na 2 SO 4
2NaOH+NO+NO2→2NaNO2+H2O2NaOH+NO+NO 2 →2NaNO 2 +H 2 O
2NaNO2+O2→2NaNO3 2NaNO 2 +O 2 →2NaNO 3
Ca(OH)2+Na2SO3→CaSO3↓+2NaOHCa(OH) 2 +Na 2 SO 3 →CaSO 3 ↓+2NaOH
Ca(OH)2+Na2SO4→CaSO4↓+2NaOHCa(OH) 2 +Na 2 SO 4 →CaSO 4 ↓+2NaOH
2CaSO3+O2→2CaSO4 2CaSO 3 +O 2 →2CaSO 4
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