CN206355802U - A kind of hydrogen peroxide method flue gas desulfurization processing system - Google Patents
A kind of hydrogen peroxide method flue gas desulfurization processing system Download PDFInfo
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- 238000006477 desulfuration reaction Methods 0.000 title claims abstract description 64
- 230000023556 desulfurization Effects 0.000 title claims abstract description 64
- MHAJPDPJQMAIIY-UHFFFAOYSA-N Hydrogen peroxide Chemical compound OO MHAJPDPJQMAIIY-UHFFFAOYSA-N 0.000 title claims abstract description 63
- UGFAIRIUMAVXCW-UHFFFAOYSA-N Carbon monoxide Chemical compound [O+]#[C-] UGFAIRIUMAVXCW-UHFFFAOYSA-N 0.000 title claims abstract description 27
- 239000003546 flue gas Substances 0.000 title claims abstract description 27
- 238000000034 method Methods 0.000 title claims description 40
- 238000010521 absorption reaction Methods 0.000 claims abstract description 113
- QAOWNCQODCNURD-UHFFFAOYSA-N Sulfuric acid Chemical compound OS(O)(=O)=O QAOWNCQODCNURD-UHFFFAOYSA-N 0.000 claims abstract description 106
- 239000007789 gas Substances 0.000 claims abstract description 48
- 238000003860 storage Methods 0.000 claims abstract description 9
- 239000012530 fluid Substances 0.000 claims 4
- UFHFLCQGNIYNRP-UHFFFAOYSA-N Hydrogen Chemical compound [H][H] UFHFLCQGNIYNRP-UHFFFAOYSA-N 0.000 claims 1
- 238000005859 coupling reaction Methods 0.000 claims 1
- 238000010790 dilution Methods 0.000 claims 1
- 239000012895 dilution Substances 0.000 claims 1
- 239000001257 hydrogen Substances 0.000 claims 1
- 229910052739 hydrogen Inorganic materials 0.000 claims 1
- 239000011800 void material Substances 0.000 claims 1
- 238000006243 chemical reaction Methods 0.000 abstract description 54
- 239000007788 liquid Substances 0.000 abstract description 15
- 238000002156 mixing Methods 0.000 abstract description 15
- 239000006227 byproduct Substances 0.000 abstract description 6
- 238000004519 manufacturing process Methods 0.000 abstract description 6
- 239000000047 product Substances 0.000 abstract description 5
- 239000002699 waste material Substances 0.000 abstract description 4
- 238000002425 crystallisation Methods 0.000 abstract description 3
- 230000008025 crystallization Effects 0.000 abstract description 3
- 238000011084 recovery Methods 0.000 abstract description 3
- RAHZWNYVWXNFOC-UHFFFAOYSA-N Sulphur dioxide Chemical compound O=S=O RAHZWNYVWXNFOC-UHFFFAOYSA-N 0.000 description 36
- 239000000571 coke Substances 0.000 description 9
- 230000008569 process Effects 0.000 description 9
- QGZKDVFQNNGYKY-UHFFFAOYSA-N Ammonia Chemical compound N QGZKDVFQNNGYKY-UHFFFAOYSA-N 0.000 description 6
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 description 6
- MWUXSHHQAYIFBG-UHFFFAOYSA-N nitrogen oxide Inorganic materials O=[N] MWUXSHHQAYIFBG-UHFFFAOYSA-N 0.000 description 6
- 239000001301 oxygen Substances 0.000 description 6
- 229910052760 oxygen Inorganic materials 0.000 description 6
- 239000002250 absorbent Substances 0.000 description 5
- 230000002745 absorbent Effects 0.000 description 5
- 239000002253 acid Substances 0.000 description 5
- PQUCIEFHOVEZAU-UHFFFAOYSA-N Diammonium sulfite Chemical compound [NH4+].[NH4+].[O-]S([O-])=O PQUCIEFHOVEZAU-UHFFFAOYSA-N 0.000 description 4
- 238000005516 engineering process Methods 0.000 description 4
- 238000012544 monitoring process Methods 0.000 description 4
- 230000003647 oxidation Effects 0.000 description 4
- 238000007254 oxidation reaction Methods 0.000 description 4
- AKEJUJNQAAGONA-UHFFFAOYSA-N sulfur trioxide Chemical compound O=S(=O)=O AKEJUJNQAAGONA-UHFFFAOYSA-N 0.000 description 4
- 229910021529 ammonia Inorganic materials 0.000 description 3
- 229910052602 gypsum Inorganic materials 0.000 description 3
- 239000010440 gypsum Substances 0.000 description 3
- 238000000746 purification Methods 0.000 description 3
- VHUUQVKOLVNVRT-UHFFFAOYSA-N Ammonium hydroxide Chemical compound [NH4+].[OH-] VHUUQVKOLVNVRT-UHFFFAOYSA-N 0.000 description 2
- 235000011114 ammonium hydroxide Nutrition 0.000 description 2
- BFNBIHQBYMNNAN-UHFFFAOYSA-N ammonium sulfate Chemical compound N.N.OS(O)(=O)=O BFNBIHQBYMNNAN-UHFFFAOYSA-N 0.000 description 2
- 229910052921 ammonium sulfate Inorganic materials 0.000 description 2
- 235000011130 ammonium sulphate Nutrition 0.000 description 2
- 230000008901 benefit Effects 0.000 description 2
- 230000015572 biosynthetic process Effects 0.000 description 2
- 230000006378 damage Effects 0.000 description 2
- 230000000694 effects Effects 0.000 description 2
- 238000004064 recycling Methods 0.000 description 2
- 230000008929 regeneration Effects 0.000 description 2
- 238000011069 regeneration method Methods 0.000 description 2
- 238000001179 sorption measurement Methods 0.000 description 2
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 2
- QGZKDVFQNNGYKY-UHFFFAOYSA-O Ammonium Chemical compound [NH4+] QGZKDVFQNNGYKY-UHFFFAOYSA-O 0.000 description 1
- DGAQECJNVWCQMB-PUAWFVPOSA-M Ilexoside XXIX Chemical compound C[C@@H]1CC[C@@]2(CC[C@@]3(C(=CC[C@H]4[C@]3(CC[C@@H]5[C@@]4(CC[C@@H](C5(C)C)OS(=O)(=O)[O-])C)C)[C@@H]2[C@]1(C)O)C)C(=O)O[C@H]6[C@@H]([C@H]([C@@H]([C@H](O6)CO)O)O)O.[Na+] DGAQECJNVWCQMB-PUAWFVPOSA-M 0.000 description 1
- QAOWNCQODCNURD-UHFFFAOYSA-L Sulfate Chemical compound [O-]S([O-])(=O)=O QAOWNCQODCNURD-UHFFFAOYSA-L 0.000 description 1
- 238000003916 acid precipitation Methods 0.000 description 1
- 238000005054 agglomeration Methods 0.000 description 1
- 230000002776 aggregation Effects 0.000 description 1
- 239000000809 air pollutant Substances 0.000 description 1
- 231100001243 air pollutant Toxicity 0.000 description 1
- 239000003513 alkali Substances 0.000 description 1
- 230000009286 beneficial effect Effects 0.000 description 1
- 230000005540 biological transmission Effects 0.000 description 1
- 230000003197 catalytic effect Effects 0.000 description 1
- 238000000354 decomposition reaction Methods 0.000 description 1
- 230000007547 defect Effects 0.000 description 1
- 230000007812 deficiency Effects 0.000 description 1
- 238000010586 diagram Methods 0.000 description 1
- 238000005265 energy consumption Methods 0.000 description 1
- 230000007613 environmental effect Effects 0.000 description 1
- 238000003912 environmental pollution Methods 0.000 description 1
- 239000011152 fibreglass Substances 0.000 description 1
- 238000010438 heat treatment Methods 0.000 description 1
- 230000006872 improvement Effects 0.000 description 1
- 239000003595 mist Substances 0.000 description 1
- 238000002360 preparation method Methods 0.000 description 1
- 230000009467 reduction Effects 0.000 description 1
- 239000011734 sodium Substances 0.000 description 1
- 229910052708 sodium Inorganic materials 0.000 description 1
- NLJMYIDDQXHKNR-UHFFFAOYSA-K sodium citrate Chemical compound O.O.[Na+].[Na+].[Na+].[O-]C(=O)CC(O)(CC([O-])=O)C([O-])=O NLJMYIDDQXHKNR-UHFFFAOYSA-K 0.000 description 1
- 239000001509 sodium citrate Substances 0.000 description 1
- 229910001220 stainless steel Inorganic materials 0.000 description 1
- 239000010935 stainless steel Substances 0.000 description 1
- XTQHKBHJIVJGKJ-UHFFFAOYSA-N sulfur monoxide Chemical class S=O XTQHKBHJIVJGKJ-UHFFFAOYSA-N 0.000 description 1
- 229910052815 sulfur oxide Inorganic materials 0.000 description 1
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- Treating Waste Gases (AREA)
Abstract
本实用新型提供一种过氧化氢法烟气脱硫处理系统。所述脱硫处理系统包括单塔四层设计的反应吸收塔,过氧化氢储存罐,循环泵,循环槽及烟囱;其中反应吸收塔四层为除雾层即吸收塔第一层、循环液室即吸收塔第二层、吸收层即吸收塔第三层和气体混合室即吸收塔第四层。本实用新型的脱硫处理系统结构简单,操作控制方便,其脱硫效率高;且处理系统配套设备少,无需额外增加操作人员,有效节约投资成本、运行成本和占地空间,能实现98%以上脱硫效率,不存在结晶堵塔问题,其副产品稀硫酸不需二次加工,回收成本低,整个生产过程中不产生新的三废产物,且无二次污染。
The utility model provides a hydrogen peroxide flue gas desulfurization treatment system. The desulfurization treatment system includes a single-tower four-layer design reaction absorption tower, a hydrogen peroxide storage tank, a circulation pump, a circulation tank and a chimney; the four layers of the reaction absorption tower are the demisting layer, that is, the first layer of the absorption tower, the circulation liquid chamber That is, the second layer of the absorption tower, the absorption layer is the third layer of the absorption tower, and the gas mixing chamber is the fourth layer of the absorption tower. The desulfurization treatment system of the utility model has simple structure, convenient operation and control, and high desulfurization efficiency; and the treatment system has few supporting equipment, no need for additional operators, effectively saving investment costs, operating costs and occupied space, and can achieve desulfurization of more than 98%. High efficiency, there is no problem of crystallization tower blockage, its by-product dilute sulfuric acid does not need secondary processing, the recovery cost is low, and no new three waste products are produced during the entire production process, and there is no secondary pollution.
Description
技术领域technical field
本实用新型属于烟气脱硫技术领域,具体涉及一种过氧化氢法烟气脱硫处理系统。The utility model belongs to the technical field of flue gas desulfurization, in particular to a hydrogen peroxide method flue gas desulfurization treatment system.
背景技术Background technique
众所周知,硫氧化物及氮氧化物已成为我国主要大气污染物,并以酸雨、雾霾等多种形式对生态环境造成严重破坏,对整个国民经济造成极大负面影响,对人们的工作生活造成极大危害。我国二氧化硫(SO2)的主要来源是我国庞大的硫酸市场需求及部分相关工业企业生产副产物中排放的二氧化硫,对硫酸尾气中的二氧化硫进行处理是关系到环境保护与经济效益的大问题,也是我国SO2减排的重点。As we all know, sulfur oxides and nitrogen oxides have become the main air pollutants in our country, and they have caused serious damage to the ecological environment in various forms such as acid rain and smog, and have had a great negative impact on the entire national economy. Great harm. The main source of sulfur dioxide (SO 2 ) in China is the huge market demand for sulfuric acid in China and the sulfur dioxide discharged from the production by-products of some related industrial enterprises. The treatment of sulfur dioxide in sulfuric acid tail gas is a major issue related to environmental protection and economic benefits. The focus of China's SO 2 emission reduction.
当前我国硫酸行业针对硫酸尾气脱硫处理的方法和处理系统设备较多,其方法包括有氨-酸法、氨法、钠碱法、柠檬酸钠法、石灰石-石膏法、活性焦法等,其中应用最广泛的有氨-酸法、石灰石-石膏法和活性焦法几种。而从已产业化的脱硫处理系统和设备来看,均存在占地面积大、运行费用高、吸收塔易堵塞、脱硫副产物难以处置等缺陷;而二次污染问题严重的石灰石-石膏法及其设备由于历史原因,仍占绝对主导地位。尽管脱硫技术经过国内外的不断改进及工程实践,且现有活性焦法脱硫技术已经相当成熟,特别是在西部缺水地区,活性焦法脱硫技术应该是很好的一种选择。但该方法对比新型催化法技术,存在所用活性焦易磨损,易烧焦、结块,加热再生过程中能耗高,运行成本高等问题。而氨-酸法脱硫存在氨泄漏、脱硫率不高,产品硫铵工艺流程长且操作复杂,生产中还伴生一些亚硫酸铵,亚硫酸铵本身不太稳定,受到阳光照射或撞击后部分会分解产生SO2和CO2,形成二次污染。At present, my country's sulfuric acid industry has many methods and treatment system equipment for sulfuric acid tail gas desulfurization treatment. The methods include ammonia-acid method, ammonia method, sodium alkali method, sodium citrate method, limestone-gypsum method, activated coke method, etc. The most widely used methods are ammonia-acid method, limestone-gypsum method and activated coke method. From the perspective of industrialized desulfurization treatment systems and equipment, there are defects such as large area, high operating costs, easy blockage of absorption towers, and difficult disposal of desulfurization by-products; and the limestone-gypsum method and Due to historical reasons, its equipment still occupies an absolute dominant position. Although the desulfurization technology has undergone continuous improvement and engineering practice at home and abroad, and the existing activated coke desulfurization technology is quite mature, especially in the water-scarce western regions, the activated coke desulfurization technology should be a good choice. However, compared with the new catalytic technology, this method has the problems of easy wear, burning and agglomeration of the active coke used, high energy consumption during heating and regeneration, and high operating costs. However, the ammonia-acid desulfurization method has ammonia leakage and low desulfurization rate. The product ammonium sulfate process is long and complicated to operate. Some ammonium sulfite is also produced in the production. Ammonium sulfite itself is not very stable. Decomposition produces SO 2 and CO 2 , forming secondary pollution.
专利申请号201310371346.8,名称为“用于不同烟气活性焦高效节能脱硫净化系统及方法”的发明专利,所述脱硫净化系统包括第一吸附脱硫段,第二吸附脱硫段,活性焦再生段和活性焦输送设备;尽管该净化系统和方法其脱硫率较高,但存在占地面积大,运行成本高,活性焦易磨损的问题。Patent application number 201310371346.8, titled "High-efficiency energy-saving desulfurization purification system and method for different flue gas activated coke", the desulfurization purification system includes the first adsorption desulfurization section, the second adsorption desulfurization section, the active coke regeneration section and Active coke conveying equipment; although the purification system and method have a high desulfurization rate, it has the problems of large footprint, high operating cost, and easy wear of active coke.
专利申请号201420140181.3,名称为“氨法烟气脱硫装置”的实用新型专利,其结构包括烟道、脱硫塔、氨水循环系统和氧化系统。该脱硫装置中,二氧化硫与氨水反应生成的烟硫酸铵,再经氧化系统氧化为硫酸铵。所述氧化系统存在氧化不完全,会伴生一些亚硫酸铵的缺点,亚硫酸铵本身不太稳定,同样受到阳光照射或撞击后就可能会分解产生SO2和CO2,形成二次污染,从而进一步造成环境污染的恶性循环。Patent application number 201420140181.3, a utility model patent named "Ammonia flue gas desulfurization device", its structure includes a flue, a desulfurization tower, an ammonia water circulation system and an oxidation system. In the desulfurization device, sulfur dioxide and ammonia water react to form ammonium nicotinic sulfate, which is then oxidized into ammonium sulfate through an oxidation system. The oxidation system has incomplete oxidation, which will be accompanied by some disadvantages of ammonium sulfite. Ammonium sulfite itself is not very stable. It may also be decomposed to produce SO 2 and CO 2 after being irradiated by sunlight or impacted, forming secondary pollution, thereby Further cause a vicious circle of environmental pollution.
发明内容Contents of the invention
本实用新型的目的正是针对上述现有技术中所存在的问题和不足,提供一种过氧化氢法烟气脱硫处理系统。所述脱硫处理系统中反应吸收塔为单塔四层设计,整个处理系统配套设备少而精,无需额外增加操作人员,有效节约投资成本、运行成本和占地空间,能实现98%以上脱硫效率,不存在结晶堵塔问题,生产过程中不产生新的三废产物,且无二次污染。The purpose of this utility model is to provide a hydrogen peroxide flue gas desulfurization treatment system aimed at the problems and deficiencies in the above-mentioned prior art. The reaction absorption tower in the desulfurization treatment system is a single-tower four-story design, and the supporting equipment of the whole treatment system is small and precise, without additional operators, which effectively saves investment costs, operating costs and floor space, and can achieve a desulfurization efficiency of over 98%. , there is no problem of crystallization tower plugging, no new three waste products are produced during the production process, and there is no secondary pollution.
为实现上述发明目的,本实用新型采用由如下的技术措施构成的技术方案来实现的。In order to realize the above-mentioned purpose of the invention, the utility model adopts the technical scheme that is made up of following technical measure to realize.
本实用新型所述一种过氧化氢法烟气脱硫处理系统,包括反应吸收塔、过氧化氢储存罐,输送管道,循环泵,循环槽和烟囱;其中,所述反应吸收塔采用单塔四层设计:四层为除雾层即吸收塔第一层,除雾层紧邻循环液室即吸收塔第二层,循环液室紧邻吸收层即吸收塔第三层,吸收层紧邻气体混合室即吸收塔第四层;所述过氧化氢储存罐置于反应吸收塔下部左外侧,通过输入管道与反应吸收塔底部气体混合室连接,气体混合室与反应吸收塔下部右外侧循环泵连接,循环泵与反应吸收塔中部右外侧循环槽连接,循环槽连接反应吸收塔中循环液室,所述烟囱安装于反应吸收塔顶部外侧,烟气通过除雾层后经输送管道由烟囱排放至大气中。A hydrogen peroxide flue gas desulfurization treatment system described in the utility model includes a reaction absorption tower, a hydrogen peroxide storage tank, a delivery pipeline, a circulation pump, a circulation tank and a chimney; wherein, the reaction absorption tower adopts a single tower four Layer design: The fourth layer is the demister layer, which is the first layer of the absorption tower. The demist layer is adjacent to the circulating liquid chamber, which is the second layer of the absorption tower. The circulating liquid chamber is adjacent to the absorption layer, which is the third layer of the absorption tower. The absorption layer is adjacent to the gas mixing chamber. The fourth floor of the absorption tower; the hydrogen peroxide storage tank is placed on the left outer side of the lower part of the reaction absorption tower, and is connected to the gas mixing chamber at the bottom of the reaction absorption tower through an input pipeline, and the gas mixing chamber is connected to the right outer circulation pump of the lower part of the reaction absorption tower, and the circulation The pump is connected to the right outer circulation tank in the middle of the reaction absorption tower, and the circulation tank is connected to the circulation liquid chamber in the reaction absorption tower. The chimney is installed outside the top of the reaction absorption tower, and the flue gas passes through the demist layer and is discharged from the chimney to the atmosphere .
本实用新型上述方案中,所述反应吸收塔的单塔四层设计为大开孔率填料塔或空塔。In the above scheme of the utility model, the four-layer single tower of the reaction absorption tower is designed as a packed tower or an empty tower with a large opening ratio.
本实用新型上述方案中,所述除雾层即吸收塔第一层中安装有除雾器。In the above solution of the utility model, the demisting layer, that is, the first layer of the absorption tower is equipped with a demister.
本实用新型上述方案中,所述循环液室即吸收塔第二层中安装有若干稀硫酸溶液喷头。In the above scheme of the utility model, several dilute sulfuric acid solution nozzles are installed in the second layer of the absorption tower in the said circulating liquid chamber.
本实用新型所述过氧化氢法烟气脱硫处理系统采用PLC即可编程逻辑控制器的控制系统进行控制,控制室不需设置常规监视设备,装置的监视与控制均通过PLC来实现。The hydrogen peroxide method flue gas desulfurization treatment system of the utility model is controlled by a control system of a programmable logic controller (PLC), and the control room does not need to be equipped with conventional monitoring equipment, and the monitoring and control of the device are all realized by PLC.
本实用新型所述脱硫处理系统中,所用过氧化氢脱硫活性强、反应速率快,二氧化硫的排放浓度低于200mg/m3以下,远低于国家标准GB26132-2010的要求,脱硫率可达98%以上,对氮氧化物亦有较高的脱除效率,且脱硫脱硝可同时进行。所述脱硫处理系统中,由于反应吸收塔采用单塔四层设计,因此脱硫处理系统配套设备少而精,无需额外增加操作人员,有效节约投资成本、运行成本和占地空间,整个生产过程中不产生新的三废产物,且无二次污染。In the desulfurization treatment system described in the utility model, the hydrogen peroxide desulfurization activity used is strong, the reaction rate is fast, the emission concentration of sulfur dioxide is lower than 200 mg/m 3 , far below the requirements of the national standard GB26132-2010, and the desulfurization rate can reach 98 It also has high removal efficiency for nitrogen oxides, and desulfurization and denitrification can be carried out at the same time. In the desulfurization treatment system, since the reaction absorption tower adopts a single-tower four-layer design, the supporting equipment of the desulfurization treatment system is small and precise, and there is no need for additional operators, which effectively saves investment costs, operating costs and floor space. During the entire production process No new three waste products are generated, and there is no secondary pollution.
本实用新型与现有技术相比具有的优点及有益的技术效果如下:Compared with the prior art, the utility model has advantages and beneficial technical effects as follows:
1、本实用新型所述的一种过氧化氢法烟气脱硫处理系统采用单塔四层设计,该反应吸收塔吸收反应和副产品的回收均在一个塔内,配套设备少而精,且可操作性强,无需额外增加操作人员,有效节约投资成本、运行成本和占地空间。1. The hydrogen peroxide method flue gas desulfurization treatment system described in this utility model adopts a single-tower four-layer design. The absorption reaction of the reaction absorption tower and the recovery of by-products are all in one tower, and the supporting equipment is small and precise, and can Strong operability, no need to add additional operators, effectively saving investment costs, operating costs and floor space.
2、本实用新型所述的一种过氧化氢法烟气脱硫处理系统,所述脱硫处理系统中脱硫副产品为稀硫酸,与传统处理系统相比不存在结晶堵塔的问题。2. A hydrogen peroxide flue gas desulfurization treatment system described in the utility model, the desulfurization by-product in the desulfurization treatment system is dilute sulfuric acid, and there is no problem of crystallization tower blockage compared with the traditional treatment system.
3、本实用新型所述的一种过氧化氢法烟气脱硫处理系统中吸收塔为大开孔率填料塔或空塔,其系统阻力小于≤600Pa,因此可节省系统动力消耗。3. The absorption tower in the hydrogen peroxide flue gas desulfurization treatment system described in this utility model is a packed tower or an empty tower with a large opening ratio, and its system resistance is less than or equal to 600 Pa, so the power consumption of the system can be saved.
4、本实用新型所述过氧化氢法烟气脱硫处理系统中,所产生的稀硫酸直接返回至反应吸收塔中用于调节酸浓度,副产品不需二次加工,回收成本大大降低;整个生产过程中不产生新的三废产物,因而无二次污染,属典型的清洁脱硫处理系统。4. In the hydrogen peroxide method flue gas desulfurization treatment system described in the utility model, the dilute sulfuric acid produced is directly returned to the reaction absorption tower to adjust the acid concentration, the by-products do not need secondary processing, and the recovery cost is greatly reduced; the entire production No new three waste products are produced in the process, so there is no secondary pollution, and it is a typical clean desulfurization treatment system.
附图说明Description of drawings
图1为本实用新型所述一种过氧化氢法烟气脱硫处理系统的整体结构示意图。Fig. 1 is a schematic diagram of the overall structure of a hydrogen peroxide method flue gas desulfurization treatment system described in the present invention.
图中,1反应吸收塔,2除雾层即吸收塔第一层,3循环液室即吸收塔第二层,4吸收层即吸收塔第三层,5气体混合室即吸收塔第四层,6过氧化氢储存罐,7输送管道,8除雾器,9稀硫酸溶液喷头,10循环泵,11循环槽,12烟囱。In the figure, 1 is the reaction absorption tower, 2 is the defogging layer, which is the first layer of the absorption tower, 3 is the second layer of the absorption tower, 4 is the second layer of the absorption tower, 4 is the third layer of the absorption tower, 5 is the fourth layer of the absorption tower, and 5 is the gas mixing chamber , 6 hydrogen peroxide storage tanks, 7 delivery pipes, 8 mist eliminators, 9 dilute sulfuric acid solution nozzles, 10 circulation pumps, 11 circulation tanks, and 12 chimneys.
具体实施方式detailed description
下面结合附图并通过具体实施方式对本实用新型作进一步的详细说明,但并不意味着是对本实用新型保护范围的任何限定。The utility model will be further described in detail below in conjunction with the accompanying drawings and specific embodiments, but it does not mean any limitation to the protection scope of the utility model.
本实用新型所述一种过氧化氢法烟气脱硫处理系统,其结构如图1所示,包括反应吸收塔1、过氧化氢储存罐6,输送管道7,循环泵10,循环槽11和烟囱12;其中,所述反应吸收塔1采用单塔四层设计,包括其中部除雾层2即吸收塔第一层,除雾层2紧邻其中部循环液室3即吸收塔第二层,循环液室3紧邻其中部吸收层4即吸收塔第三层,吸收层4紧邻其底部气体混合室5即吸收塔第四层;所述过氧化氢储存罐6置于反应吸收塔1下部左侧外,通过输送管道7与反应吸收塔1底部的气体混合室5连接,气体混合室5经输送管道7与反应吸收塔1下部右侧外安装的循环泵10连接,循环泵10经输送管道7与反应吸收塔1中部右侧外设计的循环槽11连接,循环槽11经输送管道7连接于反应吸收塔中循环液室3内安装的若干稀硫酸溶液喷头9,所述除雾层2内设置一除雾器8,反应吸收塔顶部外侧安装烟囱12,反应吸收塔内烟气通过除雾层2后经连接烟囱的输送管道排放至大气中。A hydrogen peroxide flue gas desulfurization treatment system described in the utility model has a structure as shown in Figure 1, including a reaction absorption tower 1, a hydrogen peroxide storage tank 6, a delivery pipeline 7, a circulation pump 10, a circulation tank 11 and Chimney 12; wherein, the reaction absorption tower 1 adopts a single-tower four-layer design, including the middle demister layer 2, which is the first layer of the absorption tower, and the demist layer 2 is close to the middle circulating liquid chamber 3, which is the second layer of the absorption tower, The circulating liquid chamber 3 is adjacent to the absorption layer 4 in the middle, which is the third layer of the absorption tower, and the absorption layer 4 is adjacent to the gas mixing chamber 5 at the bottom, which is the fourth layer of the absorption tower; the hydrogen peroxide storage tank 6 is placed on the left side of the lower part of the reaction absorption tower 1 The side is connected to the gas mixing chamber 5 at the bottom of the reaction absorption tower 1 through the delivery pipeline 7, and the gas mixing chamber 5 is connected to the circulation pump 10 installed outside the right side of the bottom of the reaction absorption tower 1 through the delivery pipeline 7, and the circulation pump 10 is connected through the delivery pipeline 7 is connected to the circulation tank 11 designed outside the right side of the middle part of the reaction absorption tower 1, and the circulation tank 11 is connected to several dilute sulfuric acid solution nozzles 9 installed in the circulation liquid chamber 3 in the reaction absorption tower through the delivery pipeline 7, and the demisting layer 2 A demister 8 is arranged inside, and a chimney 12 is installed on the outside of the top of the reaction absorption tower, and the flue gas in the reaction absorption tower passes through the demister layer 2 and is discharged into the atmosphere through the conveying pipeline connected to the chimney.
实施例1Example 1
本实施例按图1所述脱硫处理系统结构连接好各仪器设备,利用该脱硫处理系统按照以下脱硫处理工艺步骤及所述参数进行操作;整个操作过程采用PLC即可编程逻辑控制器的控制系统进行控制,控制室不需设置常规监视设备,装置的监视与控制均通过PLC来实现。This embodiment connects each instrument and equipment according to the structure of the desulfurization treatment system described in Figure 1, and utilizes the desulfurization treatment system to operate according to the following desulfurization treatment process steps and the described parameters; the whole operation process adopts the control system of a programmable logic controller (PLC). For control, the control room does not need to set up conventional monitoring equipment, and the monitoring and control of the device are all realized by PLC.
使用所述一种过氧化氢法烟气脱硫处理系统采用以下工艺步骤脱除二氧化硫:Using the hydrogen peroxide method flue gas desulfurization treatment system adopts the following process steps to remove sulfur dioxide:
(1)调节硫酸尾气参数(1) Adjust sulfuric acid tail gas parameters
在硫酸尾气进入反应吸收塔前,调节好硫酸尾气温度,压力,氧气含量各参数,使硫酸尾气符合脱硫要求;Before the sulfuric acid tail gas enters the reaction absorption tower, adjust the temperature, pressure and oxygen content of the sulfuric acid tail gas to make the sulfuric acid tail gas meet the desulfurization requirements;
(2)混合气体形成(2) Mixed gas formation
将步骤(1)调节好参数的硫酸尾气通入反应吸收塔中气体混合室即吸收塔第四层,将过氧化氢储存罐中的过氧化氢通过输送管道送入反应吸收塔中气体混合室后分解产生水和氧气,产生的氧气和硫酸尾气在反应吸收塔中气体混合室中混合接触反应,形成含有三氧化硫的混合气体;Pass the sulfuric acid tail gas with adjusted parameters in step (1) into the gas mixing chamber in the reaction absorption tower, that is, the fourth layer of the absorption tower, and send the hydrogen peroxide in the hydrogen peroxide storage tank into the gas mixing chamber in the reaction absorption tower through the delivery pipeline After decomposing to produce water and oxygen, the produced oxygen and sulfuric acid tail gas are mixed and contacted in the gas mixing chamber in the reaction absorption tower to form a mixed gas containing sulfur trioxide;
(3)去除二氧化硫(3) Removal of sulfur dioxide
经步骤(2)形成的混合气体与反应吸收塔中循环液室即吸收塔第二层中的稀硫酸溶液喷头喷淋而下的稀硫酸溶液在反应吸收塔中吸收层即吸收塔第三层混合接触,接触后的硫酸尾气则溶于稀硫酸中并落入反应吸收塔底部,此时二氧化硫得到去除;所述稀硫酸溶液为经脱硫处理系统产生,由循环泵经输送管道输送至反应吸收塔外的循环槽后再输送至循环液室;The mixed gas formed in step (2) and the dilute sulfuric acid solution in the second layer of the absorption tower are sprayed with the circulating liquid chamber in the reaction absorption tower, which is the third layer of the absorption tower. After mixing and contacting, the sulfuric acid tail gas after contact is dissolved in dilute sulfuric acid and falls into the bottom of the reaction absorption tower, at which time sulfur dioxide is removed; The circulating tank outside the tower is then sent to the circulating liquid chamber;
(4)稀硫酸溶液的循环利用(4) Recycling of dilute sulfuric acid solution
将步骤(3)产生的稀硫酸溶液,从反应吸收塔底部经输送管道由循环泵外排至循环槽内;调节循环槽内稀硫酸浓度,当其浓度达到2.90%后,循环回流至反应吸收塔中循环液室的稀硫酸溶液再经稀硫酸溶液喷头喷淋而下与混合气体在反应吸收塔中吸收层混合接触;循环上述步骤(3)过程,以达到二氧化硫的去除;The dilute sulfuric acid solution produced in step (3) is discharged from the bottom of the reaction absorption tower through the delivery pipeline to the circulation tank by the circulation pump; the concentration of the dilute sulfuric acid in the circulation tank is adjusted, and when the concentration reaches 2.90%, it is circulated back to the reaction absorption The dilute sulfuric acid solution in the circulating liquid chamber in the tower is then sprayed down by the dilute sulfuric acid solution nozzle and mixed with the mixed gas in the absorption layer in the reaction absorption tower to mix and contact; the process of the above step (3) is circulated to achieve the removal of sulfur dioxide;
(5)达标烟气排放至大气中(5) Up to the standard flue gas is discharged into the atmosphere
所述硫酸尾气经步骤(1)—(4)净化后通过反应吸收塔中除雾层即吸收塔第一层安装的除雾器除水干燥后,达到排放标准的烟气经反应吸收塔顶部连接的输送管道送入烟囱排放至大气中。After the sulfuric acid tail gas is purified by steps (1)-(4), it passes through the demister layer in the reaction absorption tower, that is, the demister installed on the first layer of the absorption tower is dewatered and dried, and the flue gas that reaches the emission standard passes through the top of the reaction absorption tower. The connected delivery pipe is sent to the chimney for discharge to the atmosphere.
本实施例硫酸尾气进气的二氧化硫含量为1600mg/Nm3,调节硫酸尾气温度为60℃,进气压力为1500Pa,氧气含量为4%,所用过氧化氢溶液吸收剂浓度为0.1%。In this embodiment, the sulfur dioxide content of the sulfuric acid tail gas intake is 1600mg/ Nm3 , the temperature of the sulfuric acid tail gas is adjusted to 60°C, the inlet pressure is 1500Pa, the oxygen content is 4%, and the concentration of the hydrogen peroxide solution absorbent used is 0.1%.
所用的反应吸收塔参数为反应吸收塔直径D=4.8m的填料塔,高度H=15.5m;所用循环泵为杨程30m,流量为300m3/h的904L卧式离心泵两台(一用一备);所用输送管道选用玻璃钢或不锈钢材质。The used reaction absorption tower parameter is the packed tower of reaction absorption tower diameter D=4.8m, and height H=15.5m; The circulation pump used is two sets of 904L horizontal centrifugal pumps with a lift length of 30m and a flow rate of 300m 3 /h (one with One preparation); the transmission pipeline used is made of glass fiber reinforced plastic or stainless steel.
本实施例使用所述脱硫处理系统脱除二氧化硫的具体操作过程及步骤如下:The specific operation process and steps of using the desulfurization treatment system to remove sulfur dioxide in this embodiment are as follows:
(1)、调节硫酸尾气参数(1), adjust sulfuric acid tail gas parameters
将调节好各参数的硫酸尾气通入反应吸收塔1底部气体混合室5即吸收塔第四层;Pass the sulfuric acid tail gas with adjusted parameters into the gas mixing chamber 5 at the bottom of the reaction absorption tower 1, which is the fourth layer of the absorption tower;
(2)、混合气体形成(2), mixed gas formation
将储存在过氧化氢储存罐6中的其浓度为27.5%的过氧化氢溶液吸收剂经输送管道7输送至反应吸收塔1底部气体混合室5,并分解产生水和氧气,步骤1通入的硫酸尾气与氧气在气体混合室5混合接触反应后,生成含有三氧化硫的混合气体;Its concentration that is stored in the hydrogen peroxide storage tank 6 is that the hydrogen peroxide solution absorbent of 27.5% is transported to the gas mixing chamber 5 at the bottom of the reaction absorption tower 1 through the delivery pipeline 7, and decomposes to produce water and oxygen, and step 1 feeds After the sulfuric acid tail gas and oxygen are mixed and contacted in the gas mixing chamber 5, a mixed gas containing sulfur trioxide is generated;
(3)、去除二氧化硫(3), removal of sulfur dioxide
经步骤(2)所述混合气体与反应吸收塔1中循环液室3即吸收塔第二层的稀硫酸溶液喷头9喷淋而下的稀硫酸溶液在反应吸收塔1吸收层4即吸收塔第三层混合接触,接触后的硫酸尾气则溶于稀硫酸中并落入反应吸收塔1底部,而接触后的硫酸尾气以1:40体积比溶于稀硫酸中,此时二氧化硫得到去除;所述稀硫酸溶液为经脱硫处理系统产生,由反应吸收塔底部外的循环泵10经输送管道7输送至反应吸收塔中部外的循环槽11后再经输送管道输送至循环液室3;The dilute sulfuric acid solution sprayed down by the mixed gas in the step (2) and the circulating liquid chamber 3 in the reaction absorption tower 1, that is, the dilute sulfuric acid solution nozzle 9 on the second floor of the absorption tower, is in the reaction absorption tower 1 absorption layer 4, that is, the absorption tower The third layer is mixed and contacted, the sulfuric acid tail gas after contact is dissolved in dilute sulfuric acid and falls into the bottom of reaction absorption tower 1, and the sulfuric acid tail gas after contact is dissolved in dilute sulfuric acid with a volume ratio of 1:40, and sulfur dioxide is removed at this time; The dilute sulfuric acid solution is produced by the desulfurization treatment system, and is transported to the circulation tank 11 outside the middle part of the reaction absorption tower by the circulation pump 10 outside the bottom of the reaction absorption tower through the delivery pipeline 7, and then delivered to the circulation liquid chamber 3 through the delivery pipeline;
(4)稀硫酸溶液的循环利用(4) Recycling of dilute sulfuric acid solution
将步骤(3)所述的稀硫酸溶液,从反应吸收塔1底部经循环泵10外排至循环槽11内;调节循环槽11内稀硫酸浓度,当其浓度调节到2.90%后,循环回流至反应吸收塔1中循环液室3的稀硫酸溶液再经稀硫酸溶液喷头喷淋而下与混合气体在反应吸收塔中吸收层4混合接触,循环上述步骤3过程,使反应吸收塔中循环液室3的硫酸浓度保持在20%内,以达到吸收要求的酸浓度;从而达到二氧化硫的去除;The dilute sulfuric acid solution described in step (3) is discharged into the circulation tank 11 from the bottom of the reaction absorption tower 1 through the circulation pump 10; the concentration of the dilute sulfuric acid in the circulation tank 11 is adjusted, and when the concentration is adjusted to 2.90%, the circulation is refluxed The dilute sulfuric acid solution to the circulating liquid chamber 3 in the reaction absorption tower 1 is then sprayed through the dilute sulfuric acid solution nozzle and mixed with the mixed gas in the absorption layer 4 of the reaction absorption tower, and the process of the above step 3 is circulated to circulate in the reaction absorption tower. The concentration of sulfuric acid in the liquid chamber 3 is kept within 20% to achieve the acid concentration required for absorption; thereby achieving the removal of sulfur dioxide;
(5)达标烟气排放至大气中(5) Up to the standard flue gas is discharged into the atmosphere
所述硫酸尾气经步骤(1)—(4)净化后通过反应吸收塔中除雾层2即吸收塔第一层内安装的除雾器8除水干燥后,达到排放标准的烟气经反应吸收塔1顶部连接的输送管道送入烟囱排放至大气中。After the sulfuric acid tail gas is purified by steps (1)-(4), it passes through the demister layer 2 in the reaction absorption tower, that is, the demister 8 installed in the first layer of the absorption tower is dewatered and dried, and the flue gas that reaches the emission standard is reacted The delivery pipeline connected to the top of the absorption tower 1 is sent into the chimney and discharged into the atmosphere.
本实用新型通过实施例1的脱硫处理工艺和脱硫处理系统进行脱硫脱硝操作时,其中所用吸收剂为27.5%的过氧化氢溶液,所述稀硫酸溶液浓度控制在不低于2.90%,反应吸收塔1吸收层4中过氧化氢最终浓度为0.1%,吸收层内硫酸浓度保持在20%,硫酸尾气进气温度为60℃,压力为1500Pa,硫酸尾气进气二氧化硫含量为1600mg/Nm3。经脱硫系统处理后二氧化硫浓度小于200mg/Nm3,脱硫率大于98%。When the utility model carries out the desulfurization and denitrification operation through the desulfurization treatment process and desulfurization treatment system of Example 1, the absorbent used is 27.5% hydrogen peroxide solution, and the concentration of the dilute sulfuric acid solution is controlled at not less than 2.90%, and the reaction absorbs The final concentration of hydrogen peroxide in the absorption layer 4 of tower 1 is 0.1%, the concentration of sulfuric acid in the absorption layer is kept at 20%, the inlet temperature of the sulfuric acid tail gas is 60°C, the pressure is 1500Pa, and the sulfur dioxide content of the inlet gas of the sulfuric acid tail gas is 1600mg/ Nm3 . After being treated by the desulfurization system, the concentration of sulfur dioxide is less than 200mg/Nm 3 , and the desulfurization rate is greater than 98%.
实施例2Example 2
本实施例同样按图1所示结构连接好各仪器设备,其所用仪器设备和操作过程及步骤与实施例1相同,和实施例1不同之处在于,所述硫酸尾气进气温度为70℃,反应吸收塔1吸收层4中过氧化氢溶液吸收剂浓度为0.5%,吸收层内硫酸浓度保持在25%,其他所用参数与实施例1均相同。经脱硫系统处理后其二氧化硫浓度小于200mg/Nm3,脱硫率大于98%。This embodiment also connects each instrument and equipment according to the structure shown in Figure 1, and the instruments and equipment used, the operation process and the steps are the same as in Example 1, and the difference from Example 1 is that the inlet temperature of the sulfuric acid tail gas is 70°C , hydrogen peroxide solution absorbent concentration is 0.5% in the absorption layer 4 of reaction absorption tower 1, and sulfuric acid concentration remains on 25% in the absorption layer, and other used parameters are all identical with embodiment 1. After being treated by the desulfurization system, the concentration of sulfur dioxide is less than 200mg/Nm 3 , and the desulfurization rate is greater than 98%.
实施例3Example 3
本实施例同样按图1所示结构连接好各仪器设备,其所用仪器设备和操作过程及步骤与实施例1相同,不同之处在于,所述硫酸尾气进气温度为80℃,反应吸收塔1吸收层4中过氧化氢溶液吸收剂浓度为1%,吸收层4内硫酸浓度保持在30%。经脱硫系统处理后其二氧化硫浓度小于200mg/Nm3,脱硫率大于98%。This embodiment also connects each instrument and equipment according to the structure shown in Figure 1, and the instrument and equipment used, the operation process and the steps are the same as in Example 1, the difference is that the inlet temperature of the sulfuric acid tail gas is 80 ° C, and the reaction absorption tower 1 The hydrogen peroxide solution absorbent concentration in the absorption layer 4 is 1%, and the sulfuric acid concentration in the absorption layer 4 is maintained at 30%. After being treated by the desulfurization system, the concentration of sulfur dioxide is less than 200mg/Nm 3 , and the desulfurization rate is greater than 98%.
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CN107899403A (en) * | 2017-11-30 | 2018-04-13 | 成武县晨晖环保科技有限公司 | Chloroethene acylating acid method produces the tail gas sulphur dioxide sulfur method of chloracetyl chloride |
CN114634832A (en) * | 2022-03-11 | 2022-06-17 | 山西农业大学 | Biological denitrification device for biogas |
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CN107890763A (en) * | 2017-11-30 | 2018-04-10 | 成武县晨晖环保科技有限公司 | A kind of chlorinated exhaust absorption process for producing trichloro-acetic chloride |
CN107899403A (en) * | 2017-11-30 | 2018-04-13 | 成武县晨晖环保科技有限公司 | Chloroethene acylating acid method produces the tail gas sulphur dioxide sulfur method of chloracetyl chloride |
CN114634832A (en) * | 2022-03-11 | 2022-06-17 | 山西农业大学 | Biological denitrification device for biogas |
CN114634832B (en) * | 2022-03-11 | 2023-01-13 | 山西农业大学 | Biological denitrification device for biogas |
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