CN219482212U - Ammonia gas treatment equipment for cement kiln tail waste gas - Google Patents
Ammonia gas treatment equipment for cement kiln tail waste gas Download PDFInfo
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- CN219482212U CN219482212U CN202320350393.3U CN202320350393U CN219482212U CN 219482212 U CN219482212 U CN 219482212U CN 202320350393 U CN202320350393 U CN 202320350393U CN 219482212 U CN219482212 U CN 219482212U
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- QGZKDVFQNNGYKY-UHFFFAOYSA-N Ammonia Chemical compound N QGZKDVFQNNGYKY-UHFFFAOYSA-N 0.000 title claims abstract description 123
- 239000004568 cement Substances 0.000 title claims abstract description 21
- 239000002912 waste gas Substances 0.000 title claims abstract description 19
- 239000003054 catalyst Substances 0.000 claims abstract description 64
- 229910021529 ammonia Inorganic materials 0.000 claims abstract description 42
- 239000007789 gas Substances 0.000 claims abstract description 31
- 238000000354 decomposition reaction Methods 0.000 claims abstract description 23
- 238000003860 storage Methods 0.000 claims abstract description 15
- 238000001514 detection method Methods 0.000 claims abstract description 12
- 238000002156 mixing Methods 0.000 claims abstract description 12
- 238000005507 spraying Methods 0.000 claims abstract description 12
- 238000003756 stirring Methods 0.000 claims abstract description 11
- 238000005086 pumping Methods 0.000 claims abstract description 5
- 239000007921 spray Substances 0.000 claims description 16
- 239000007864 aqueous solution Substances 0.000 claims description 6
- 238000009434 installation Methods 0.000 claims description 3
- 238000000889 atomisation Methods 0.000 claims 1
- 239000003344 environmental pollutant Substances 0.000 abstract 1
- 231100000719 pollutant Toxicity 0.000 abstract 1
- 239000000243 solution Substances 0.000 description 7
- 239000002893 slag Substances 0.000 description 5
- 238000000034 method Methods 0.000 description 4
- MWUXSHHQAYIFBG-UHFFFAOYSA-N nitrogen oxide Inorganic materials O=[N] MWUXSHHQAYIFBG-UHFFFAOYSA-N 0.000 description 3
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 3
- 239000005997 Calcium carbide Substances 0.000 description 2
- 239000000809 air pollutant Substances 0.000 description 2
- 231100001243 air pollutant Toxicity 0.000 description 2
- 238000006243 chemical reaction Methods 0.000 description 2
- 238000010586 diagram Methods 0.000 description 2
- 238000005516 engineering process Methods 0.000 description 2
- 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 description 2
- 230000032258 transport Effects 0.000 description 2
- VHUUQVKOLVNVRT-UHFFFAOYSA-N Ammonium hydroxide Chemical compound [NH4+].[OH-] VHUUQVKOLVNVRT-UHFFFAOYSA-N 0.000 description 1
- 235000011114 ammonium hydroxide Nutrition 0.000 description 1
- 230000009286 beneficial effect Effects 0.000 description 1
- 229910052791 calcium Inorganic materials 0.000 description 1
- 239000011575 calcium Substances 0.000 description 1
- -1 calcium nitride Chemical class 0.000 description 1
- 238000002485 combustion reaction Methods 0.000 description 1
- 230000007613 environmental effect Effects 0.000 description 1
- 238000002347 injection Methods 0.000 description 1
- 239000007924 injection Substances 0.000 description 1
- 238000004519 manufacturing process Methods 0.000 description 1
- 238000012986 modification Methods 0.000 description 1
- 230000004048 modification Effects 0.000 description 1
- 238000012544 monitoring process Methods 0.000 description 1
- 238000005554 pickling Methods 0.000 description 1
- 238000002360 preparation method Methods 0.000 description 1
- 239000002994 raw material Substances 0.000 description 1
- 238000005406 washing Methods 0.000 description 1
- 239000002699 waste material Substances 0.000 description 1
Landscapes
- Exhaust Gas Treatment By Means Of Catalyst (AREA)
Abstract
Description
技术领域technical field
本实用新型涉及氨气的治理技术领域,尤其涉及一种水泥窑尾废气的氨气治理设备。The utility model relates to the technical field of ammonia treatment, in particular to an ammonia treatment equipment for cement kiln tail waste gas.
背景技术Background technique
《水泥工业大气污染物超低排放标准》的颁布实施,水泥企业为了氮氧化物实现超低排放,目前大多数水泥企业采用分级燃烧+SNCR系统。由于SNCR系统氨水反应不完全,导致废气中氨气排放超标;电石渣水泥生产线,由于原料的特殊性:干法电石渣制备过程中生成的氮化钙,吸收水分后会产生氨气,导致电石渣水泥窑废气中氨气浓度超标,再加SNCR系统氨逃逸的叠加,废气中氨气的排放浓度居高不下。经过对部分电石渣水泥窑废气检测发现,废气中氨气浓度可高达98ppm,折算后约75mg/Nm3,远大于《水泥工业大气污染物超低排放标准》中氨气排放≤8mg/Nm3。废气中氨气的治理势在必行。With the promulgation and implementation of the "Ultra-low Emission Standard of Air Pollutants in the Cement Industry", most cement enterprises currently adopt staged combustion + SNCR system in order to achieve ultra-low emission of nitrogen oxides. Due to the incomplete reaction of ammonia water in the SNCR system, the discharge of ammonia gas in the waste gas exceeds the standard; due to the particularity of raw materials in the carbide slag cement production line: the calcium nitride generated in the dry calcium carbide slag preparation process will produce ammonia gas after absorbing water, resulting in calcium carbide slag. The concentration of ammonia gas in the waste gas of slag cement kiln exceeds the standard, coupled with the superposition of ammonia escape in the SNCR system, the emission concentration of ammonia gas in the waste gas remains high. After testing the exhaust gas of some carbide slag cement kilns, it was found that the ammonia concentration in the exhaust gas can be as high as 98ppm, which is about 75mg/Nm 3 after conversion, which is much higher than the ammonia emission ≤ 8mg/Nm 3 in the "Ultra-low Emission Standard of Air Pollutants for the Cement Industry" . The treatment of ammonia in waste gas is imperative.
传统的氨气治理方案:水洗法,酸洗法等,投资大,且存在二次污染问题。随着国家对环保的要求进一步提升,水泥企业急需一种投资少,无二次污染,可长期稳定运行的氨气治理方案。The traditional ammonia treatment schemes: water washing method, pickling method, etc., require large investment and have secondary pollution problems. With the further improvement of the country's environmental protection requirements, cement enterprises are in urgent need of an ammonia treatment solution that requires less investment, no secondary pollution, and can operate stably for a long time.
实用新型内容Utility model content
本实用新型的目的是为了解决现有技术中存在的缺点,而提出的一种水泥窑尾废气的氨气治理设备。The purpose of the utility model is to solve the shortcomings in the prior art, and propose a kind of ammonia treatment equipment for cement kiln tail waste gas.
为了实现上述目的,本实用新型采用了如下技术方案:一种水泥窑尾废气的氨气治理设备,包括氨气分解催化剂配置、搅拌混合装置、泵力输送系统、喷雾系统、氨气检测系统以及自动控制系统,所述氨气分解催化剂配置通过泵力输送系统连接有窑尾废气烟囱,所述喷雾系统、氨气检测系统以及自动控制系统均安装在窑尾废气烟囱的适当位置,所述氨气分解催化剂配置顶部设置有搅拌混合装置;In order to achieve the above purpose, the utility model adopts the following technical scheme: a kind of ammonia treatment equipment for cement kiln exhaust gas, including ammonia decomposition catalyst configuration, stirring and mixing device, pump force delivery system, spray system, ammonia detection system and Automatic control system, the configuration of the ammonia decomposition catalyst is connected to the kiln tail exhaust gas chimney through the pump force delivery system, the spray system, the ammonia gas detection system and the automatic control system are all installed in the appropriate position of the kiln tail exhaust gas chimney, the ammonia The top of the gas decomposition catalyst configuration is equipped with a stirring and mixing device;
所述氨气分解催化剂配置包括两个催化剂储罐,一个所述催化剂储罐为低浓度催化剂水溶液,另一个所述催化剂储罐为高浓度催化剂水溶液。The ammonia decomposition catalyst configuration includes two catalyst storage tanks, one catalyst storage tank is a low-concentration catalyst aqueous solution, and the other catalyst storage tank is a high-concentration catalyst aqueous solution.
作为上述技术方案的进一步描述:As a further description of the above technical solution:
所述泵力输送系统包括手动阀、电磁阀、流量阀、输送泵、催化剂输送管道以及电控系统,所述手动阀、电磁阀、流量阀以及输送泵均设置于催化剂输送管道的外部,所述电磁阀、流量阀以及输送泵均与电控系统电性连接,所述催化剂输送管道的一端与催化剂储罐相连通,所述催化剂输送管道的另一端与窑尾废气烟囱相连通。The pump delivery system includes a manual valve, a solenoid valve, a flow valve, a delivery pump, a catalyst delivery pipeline and an electric control system, and the manual valve, a solenoid valve, a flow valve and a delivery pump are all arranged outside the catalyst delivery pipeline. The solenoid valve, flow valve and delivery pump are all electrically connected to the electric control system, one end of the catalyst delivery pipeline is connected to the catalyst storage tank, and the other end of the catalyst delivery pipeline is connected to the kiln exhaust gas chimney.
作为上述技术方案的进一步描述:As a further description of the above technical solution:
所述喷雾系统可选择在窑尾废气烟囱合适的位置根据窑尾废气烟囱直径大小均匀设置四至六杆雾化喷枪并连接有压缩空气管道。The spraying system can be selected to uniformly arrange four to six atomizing spray guns at a suitable position of the kiln tail exhaust gas chimney according to the diameter of the kiln tail exhaust gas chimney and be connected with compressed air pipes.
作为上述技术方案的进一步描述:As a further description of the above technical solution:
所述氨气检测系统在窑尾废气烟囱高出喷雾系统安装位置20米以上合适位置安装。The ammonia gas detection system is installed at a suitable position more than 20 meters above the installation position of the spray system at the kiln exhaust gas chimney.
作为上述技术方案的进一步描述:As a further description of the above technical solution:
所述泵力输送系统、喷雾系统、氨气检测系统均与自动控制系统相连。The pump force conveying system, the spray system and the ammonia detection system are all connected with the automatic control system.
本实用新型具有如下有益效果:The utility model has the following beneficial effects:
本实用新型中,通过搅拌混合装置对氨气分解催化剂配置内的催化剂进行混合,随后混合均匀的催化剂经泵力输送系统输送至安装在窑尾废气烟囱适当位置的喷雾系统,经过其雾化后和废气充分接触,实现废气中氨气的有效分解,通过氨气检测仪实时检测氨气数值,并反馈至自动控制系统,最终实现预设氨气排放浓度指标下连续稳定运行,投资少,无二次污染。In the utility model, the catalyst in the ammonia decomposition catalyst configuration is mixed by a stirring and mixing device, and then the uniformly mixed catalyst is transported to the spray system installed at the appropriate position of the kiln tail exhaust gas chimney through the pump delivery system, and after being atomized Fully contact with the exhaust gas to realize the effective decomposition of ammonia in the exhaust gas. The ammonia gas value is detected in real time by the ammonia gas detector and fed back to the automatic control system. Finally, continuous and stable operation is realized under the preset ammonia emission concentration index, with less investment and no waste. Secondary pollution.
附图说明Description of drawings
图1为本实用新型提出的一种水泥窑尾废气的氨气治理设备的治理技术流程示意图;Fig. 1 is the schematic diagram of the treatment technology process of the ammonia treatment equipment of a kind of cement kiln exhaust waste gas that the utility model proposes;
图2为本实用新型提出的一种水泥窑尾废气的氨气治理设备的治理技术喷雾系统简图。Fig. 2 is a schematic diagram of the treatment technology spraying system of the ammonia gas treatment equipment for cement kiln tail waste gas proposed by the utility model.
图例说明:illustration:
1、氨气分解催化剂配置;2、搅拌混合装置;3、手动阀;4、电磁阀;5、流量阀;6、输送泵;7、催化剂输送管道;8、氨气检测仪;9、窑尾废气烟囱;10、压缩空气管道;11、雾化喷枪。1. Ammonia decomposition catalyst configuration; 2. Stirring and mixing device; 3. Manual valve; 4. Solenoid valve; 5. Flow valve; 6. Delivery pump; 7. Catalyst delivery pipeline; 8. Ammonia detector; 9. Kiln Exhaust gas chimney; 10. Compressed air pipeline; 11. Atomizing spray gun.
具体实施方式Detailed ways
下面将结合本实用新型实施例中的附图,对本实用新型实施例中的技术方案进行清楚、完整地描述,显然,所描述的实施例仅仅是本实用新型一部分实施例,而不是全部的实施例。基于本实用新型中的实施例,本领域普通技术人员在没有做出创造性劳动前提下所获得的所有其他实施例,都属于本实用新型保护的范围。The technical solutions in the embodiments of the present invention will be clearly and completely described below in conjunction with the accompanying drawings in the embodiments of the present invention. Obviously, the described embodiments are only part of the embodiments of the present invention, not all of them. example. Based on the embodiments of the present utility model, all other embodiments obtained by persons of ordinary skill in the art without making creative efforts belong to the scope of protection of the present utility model.
参照图1-2,本实用新型提供的一种实施例:一种水泥窑尾废气的氨气治理设备,包括氨气分解催化剂配置1、搅拌混合装置2、泵力输送系统、喷雾系统、氨气检测系统以及自动控制系统,氨气分解催化剂配置1通过泵力输送系统连接有窑尾废气烟囱9,喷雾系统、氨气检测系统以及自动控制系统均安装在窑尾废气烟囱9的适当位置,氨气分解催化剂配置1顶部设置有搅拌混合装置2;Referring to Figure 1-2, an embodiment provided by the utility model: a kind of ammonia treatment equipment for cement kiln exhaust gas, including ammonia decomposition catalyst configuration 1, stirring and mixing device 2, pump delivery system, spray system, ammonia Gas detection system and automatic control system, the ammonia gas decomposition catalyst configuration 1 is connected to the kiln tail exhaust gas chimney 9 through the pump force delivery system, and the spraying system, ammonia gas detection system and automatic control system are all installed in the appropriate position of the kiln tail exhaust gas chimney 9, The top of the ammonia decomposition catalyst configuration 1 is provided with a stirring and mixing device 2;
氨气分解催化剂配置1包括两个催化剂储罐,一个催化剂储罐为低浓度催化剂水溶液,另一个催化剂储罐为高浓度催化剂水溶液,通过搅拌混合装置2对氨气分解催化剂配置1内的催化剂进行混合,随后混合均匀的催化剂经泵力输送系统输送至安装在窑尾废气烟囱9适当位置的喷雾系统,经过其雾化后和废气充分接触,实现废气中氨气的有效分解,通过氨气检测仪8实时检测氨气数值,并反馈至自动控制系统,最终实现预设氨气排放浓度指标下连续稳定运行,投资少,无二次污染,为了适应氨气浓度大幅度波动,考虑两种浓度等级,正常情况下使用含有催化剂浓度低一些的水溶液催化剂储罐,保证氨气超低排放的前提下,使得运行成本最低;氨气浓度增大较多时,使用含有催化剂浓度较大的水溶液催化剂储罐,保证氨气超低排放的前提下,防止过多的水汽凝结沉底。Ammonia decomposition catalyst configuration 1 includes two catalyst storage tanks, one catalyst storage tank is a low-concentration catalyst aqueous solution, and the other catalyst storage tank is a high-concentration catalyst aqueous solution. Mixing, and then the uniformly mixed catalyst is transported to the spray system installed at the appropriate position of the exhaust gas chimney 9 at the end of the kiln through the pumping conveying system. The instrument 8 detects the value of ammonia in real time and feeds it back to the automatic control system, and finally realizes continuous and stable operation under the preset ammonia emission concentration index, with less investment and no secondary pollution. In order to adapt to the large fluctuation of ammonia concentration, two concentrations are considered Under normal circumstances, use an aqueous catalyst storage tank with a lower catalyst concentration to ensure the lowest operating cost under the premise of ensuring ultra-low emission of ammonia gas; when the ammonia concentration increases a lot, use an aqueous catalyst storage tank with a higher concentration of catalyst Tanks, under the premise of ensuring ultra-low emission of ammonia gas, prevent excessive water vapor from condensing and sinking to the bottom.
泵力输送系统包括手动阀3、电磁阀4、流量阀5、输送泵6、催化剂输送管道7以及电控系统,手动阀3、电磁阀4、流量阀5以及输送泵6均设置于催化剂输送管道7的外部,电磁阀4、流量阀5以及输送泵6均与电控系统电性连接,催化剂输送管道7的一端与催化剂储罐相连通,催化剂输送管道7的另一端与窑尾废气烟囱9相连通,为将混合好的催化剂输送至喷雾系统,喷雾系统可选择在窑尾废气烟囱9合适的位置根据窑尾废气烟囱9直径大小均匀设置四至六杆雾化喷枪11并连接有压缩空气管道10,将催化剂通过泵力输送系统输送至喷雾系统,经过其雾化后和废气充分接触,实现废气中氨气的有效分解,实现氨气的超低排放,氨气检测系统在窑尾废气烟囱9高出喷雾系统安装位置20米以上合适位置安装,在线实时监测氨气排放浓度或排放量,并对自动控制系统提供实时控制依据,泵力输送系统、喷雾系统、氨气检测系统均与自动控制系统相连,自动控制系统,根据氨气检测系统提供的实时数据,调整催化剂的喷入量,达到预期设定的氨气排放控制指标。The pump delivery system includes manual valve 3, solenoid valve 4, flow valve 5, delivery pump 6, catalyst delivery pipeline 7 and electric control system. Manual valve 3, solenoid valve 4, flow valve 5 and delivery pump 6 are all set at the Outside the pipeline 7, the solenoid valve 4, the flow valve 5 and the delivery pump 6 are all electrically connected to the electric control system, one end of the catalyst delivery pipeline 7 is connected to the catalyst storage tank, and the other end of the catalyst delivery pipeline 7 is connected to the kiln exhaust gas chimney 9 are connected, in order to transport the mixed catalyst to the spray system, the spray system can be selected at the appropriate position of the kiln tail exhaust gas chimney 9 according to the diameter of the kiln tail exhaust gas chimney 9 and evenly set up four to six atomizing spray guns 11 and connected with compressed air The pipeline 10 transports the catalyst to the spraying system through the pumping conveying system, and after being atomized, it fully contacts with the exhaust gas to realize the effective decomposition of ammonia in the exhaust gas and the ultra-low emission of ammonia. The chimney 9 is installed at a suitable position more than 20 meters above the installation position of the spray system, and the online real-time monitoring of ammonia emission concentration or discharge volume provides real-time control basis for the automatic control system. The pump force delivery system, spray system, and ammonia gas detection system are all integrated The automatic control system is connected, and the automatic control system, according to the real-time data provided by the ammonia gas detection system, adjusts the injection amount of the catalyst to achieve the expected set ammonia emission control index.
工作原理:通过搅拌混合装置2对氨气分解催化剂配置1内的催化剂进行混合,随后混合均匀的催化剂经泵力输送系统输送至安装在窑尾废气烟囱9适当位置的喷雾系统,经过其雾化后和废气充分接触,实现废气中氨气的有效分解,通过氨气检测仪8实时检测氨气数值,并反馈至自动控制系统,最终实现预设氨气排放浓度指标下连续稳定运行,投资少,无二次污染。Working principle: The catalyst in the ammonia decomposition catalyst configuration 1 is mixed by the stirring and mixing device 2, and then the uniformly mixed catalyst is transported to the spray system installed at the appropriate position of the exhaust gas chimney 9 at the kiln tail through the pump conveying system, and atomized by it. After fully contacting with the exhaust gas, the effective decomposition of ammonia in the exhaust gas is realized. The ammonia gas value is detected in real time by the ammonia gas detector 8 and fed back to the automatic control system, and finally realizes continuous and stable operation under the preset ammonia emission concentration index, with less investment , no secondary pollution.
最后应说明的是:以上所述仅为本实用新型的优选实施例而已,并不用于限制本实用新型,尽管参照前述实施例对本实用新型进行了详细的说明,对于本领域的技术人员来说,其依然可以对前述各实施例所记载的技术方案进行修改,或者对其中部分技术特征进行等同替换,凡在本实用新型的精神和原则之内,所作的任何修改、等同替换、改进等,均应包含在本实用新型的保护范围之内。Finally, it should be noted that: the above is only a preferred embodiment of the utility model, and is not intended to limit the utility model, although the utility model has been described in detail with reference to the foregoing embodiments, for those skilled in the art , it can still modify the technical solutions recorded in the foregoing embodiments, or perform equivalent replacements on some of the technical features. Any modifications, equivalent replacements, improvements, etc. made within the spirit and principles of the present utility model, All should be included within the protection scope of the present utility model.
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