CN105107374B - Flue gas desulfurization and denitration device utilizing proton membrane electrocatalysis - Google Patents
Flue gas desulfurization and denitration device utilizing proton membrane electrocatalysis Download PDFInfo
- Publication number
- CN105107374B CN105107374B CN201510580979.9A CN201510580979A CN105107374B CN 105107374 B CN105107374 B CN 105107374B CN 201510580979 A CN201510580979 A CN 201510580979A CN 105107374 B CN105107374 B CN 105107374B
- Authority
- CN
- China
- Prior art keywords
- flue gas
- plate
- catalyst
- tower body
- hydrogen
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Expired - Fee Related
Links
Classifications
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02E—REDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
- Y02E60/00—Enabling technologies; Technologies with a potential or indirect contribution to GHG emissions mitigation
- Y02E60/30—Hydrogen technology
- Y02E60/36—Hydrogen production from non-carbon containing sources, e.g. by water electrolysis
Landscapes
- Physical Or Chemical Processes And Apparatus (AREA)
- Electrolytic Production Of Non-Metals, Compounds, Apparatuses Therefor (AREA)
Abstract
Description
技术领域technical field
本发明属于烟气脱硫脱硝装置技术领域。具体涉及一种质子膜电催化烟气脱硫脱硝装置。The invention belongs to the technical field of flue gas desulfurization and denitrification devices. Specifically relates to a proton membrane electrocatalytic flue gas desulfurization and denitrification device.
背景技术Background technique
随着我国工业化、城镇化的不断加速,工业在国民经济增长中占有越来越大的比重,人类对于能源的需求也与日俱增。煤炭、石油、天然气等自然资源的消耗日益剧增,导致了大气污染。日前,全国众多城市出现的雾霾天气,使人类的生存环境面临挑战,大气中的有害气体因其具有毒害性强、扩散波及面积广、控制难度大等特点,备受国内外各界的关注。SO2、NOX以及CO2等烟气作为主要污染物质,其中SO2、NOX会形成酸雨,亦会形成光化学烟雾等污染现象,不仅会危害人们的呼吸道系统,还会破坏植被的正常生长;而空气中释放的大量的CO2,严重影响气候变化,造成“温室效应”,所以如何有效地治理SO2、NOX以及CO2等有害烟气已成为迫在眉睫的环保问题。With the continuous acceleration of industrialization and urbanization in our country, industry occupies an increasing proportion in the growth of the national economy, and human demand for energy is also increasing day by day. The consumption of natural resources such as coal, oil, and natural gas is increasing day by day, resulting in air pollution. A few days ago, the smog weather in many cities across the country has challenged the living environment of human beings. Harmful gases in the atmosphere have attracted much attention from all walks of life at home and abroad because of their characteristics of strong toxicity, wide spread and difficulty in control. Flue gas such as SO 2 , NO X and CO 2 are the main pollutants. Among them, SO 2 and NO X will form acid rain and photochemical smog and other pollution phenomena, which will not only endanger people's respiratory system, but also destroy the normal growth of vegetation. ; and a large amount of CO 2 released in the air seriously affects climate change and causes "greenhouse effect". Therefore, how to effectively control harmful flue gases such as SO 2 , NO X and CO 2 has become an urgent environmental protection problem.
目前,对于烟气SOX的去除主要采用的是石灰石—石膏法,石灰石—石膏法在研究和环保上取得了一些成果,但是存在装置复杂,投资大,运行费用偏高的问题,当烟气中SO2波动比较大时,石灰石量难以控制,生成的CaSO3和CaSO4容易堵塞管道和设备。对于烟气NOX的去除主要采用催化还原法,催化还原法将烟气中的NOX排放浓度虽可降至较低水平,但消耗大量NH3,有的还消耗燃料气,经济亏损大。在降低CO2浓度的方法中,研究最多的还原方法有热化学还原和光催化还原等,其中热化学还原需要高温高压,而且在还原的过程中还会产生CO2;光催化还原虽然环保节能,但是产率较低,速度较慢。At present, the limestone-gypsum method is mainly used for the removal of flue gas SO X. The limestone-gypsum method has achieved some results in research and environmental protection, but there are problems of complex equipment, large investment, and high operating costs. When the flue gas When the medium SO 2 fluctuates greatly, the amount of limestone is difficult to control, and the generated CaSO 3 and CaSO 4 are easy to block pipelines and equipment. For the removal of flue gas NOx , the catalytic reduction method is mainly used. Although the catalytic reduction method can reduce the NOx emission concentration in the flue gas to a low level, it consumes a lot of NH 3 and some fuel gas, resulting in a large economic loss. Among the methods for reducing CO 2 concentration, the most studied reduction methods are thermochemical reduction and photocatalytic reduction, among which thermochemical reduction requires high temperature and high pressure, and CO 2 will be generated during the reduction process; although photocatalytic reduction is environmentally friendly and energy-saving, But the yield is lower and the speed is slower.
传统工艺多是在脱硫装置后面或在除尘器前面加装脱硝装置,从而实现联合脱硫脱硝,这种分级治理方式存在占地面积大、投资和运行费用高等诸多弊端。The traditional process is mostly to install a denitrification device behind the desulfurization device or in front of the dust collector to achieve combined desulfurization and denitrification. This hierarchical treatment method has many disadvantages such as large area occupation, high investment and operating costs.
发明内容Contents of the invention
本发明旨在克服现有技术缺陷,目的是提供一种结构简单、占地面积小、投资和运行费用低、烟气净化效率高和产物回收再利用效果好的质子膜电催化烟气脱硫脱硝装置。The present invention aims to overcome the defects of the prior art, and aims to provide a proton membrane electrocatalytic flue gas desulfurization and denitrification with simple structure, small footprint, low investment and operating costs, high flue gas purification efficiency and good product recovery and reuse effect. device.
为实现上述目的,本发明采用的技术方案是:所述装置由催化反应吸收塔和电解反应器组成,催化反应吸收塔的下端和电解反应器的上端同中心线连接为整体。In order to achieve the above object, the technical solution adopted by the present invention is: the device is composed of a catalytic reaction absorption tower and an electrolytic reactor, the lower end of the catalytic reaction absorption tower and the upper end of the electrolytic reactor are connected as a whole with the center line.
催化反应吸收塔的结构是:顶盖和塔身通过法兰同中心线固定连接,顶盖的纵截面呈圆弧状,顶盖的中心位置处设有排气口。The structure of the catalytic reaction absorption tower is: the top cover and the tower body are fixedly connected with the center line through the flange, the longitudinal section of the top cover is arc-shaped, and the center of the top cover is provided with an exhaust port.
塔身的结构是:塔身壳体为空心圆柱体,塔身壳体的高度和外径比为3︰1~5︰1。在塔身壳体内,从上端到靠近下端处依次设有挡板、第一脱硫脱硝催化剂填料层、上承接板、固碳催化剂填料层、中承接板、第二脱硫脱硝催化剂填料层、下承接板、固液分离器、烟气分散器和氢气分散器。The structure of the tower body is: the tower body shell is a hollow cylinder, and the height and outer diameter ratio of the tower body shell is 3:1~5:1. In the tower shell, there are baffles, first desulfurization and denitrification catalyst packing layer, upper receiving plate, carbon fixation catalyst packing layer, middle receiving plate, second desulfurization and denitrification catalyst packing layer, lower receiving plate from the upper end to the lower end. plate, solid-liquid separator, flue gas diffuser and hydrogen diffuser.
其中:挡板与上承接板间的距离、上承接板与中承接板间的距离和中承接板与下承接板间的距离相等;第一脱硫脱硝催化剂填料层、固碳催化剂填料层和第二脱硫脱硝催化剂填料层的填料填充率为0.9~1倍。固液分离器为斜面设置,固液分离器与水平面的夹角为15~20°,固液分离器与塔身壳体的内壁固定连接。塔身壳体的一侧开有固体产物排出口,所述塔身壳体的一侧为与固液分离器的斜面最低位置相同的一侧,固体产物排出口紧贴固液分离器的上斜面。在塔身壳体的另一侧开有烟气进气口,烟气进气口位于烟气分散器和氢气分散器之间。烟气分散器的上平面到下承接板的下平面间的距离为塔身壳体内径的0.3~0.4倍,氢气分散器的上平面到烟气分散器的下平面间的距离为塔身壳体内径的0.2~0.3倍。Among them: the distance between the baffle plate and the upper receiving plate, the distance between the upper receiving plate and the middle receiving plate, and the distance between the middle receiving plate and the lower receiving plate are equal; the first desulfurization and denitrification catalyst packing layer, the carbon fixation catalyst packing layer and the second The filler filling rate of the second desulfurization and denitrification catalyst filler layer is 0.9 to 1 times. The solid-liquid separator is set on an inclined plane, the angle between the solid-liquid separator and the horizontal plane is 15-20°, and the solid-liquid separator is fixedly connected to the inner wall of the tower shell. There is a solid product discharge port on one side of the tower shell, which is the same side as the lowest position of the slope of the solid-liquid separator, and the solid product discharge port is close to the top of the solid-liquid separator. inclined plane. A flue gas inlet is opened on the other side of the tower shell, and the flue gas inlet is located between the flue gas diffuser and the hydrogen diffuser. The distance between the upper plane of the flue gas diffuser and the lower plane of the lower receiving plate is 0.3~0.4 times the inner diameter of the tower shell, and the distance between the upper plane of the hydrogen diffuser and the lower plane of the flue gas diffuser is the tower shell 0.2~0.3 times the internal diameter.
所述电解反应器的结构是:电解反应器壳体为圆筒状,电解反应器壳体外径与塔身壳体的外径相等,电解反应器壳体的高度与外径之比为1.1︰1~1.3︰1。电解反应器壳体最上端设有引流板,引流板为斜面设置,引流板与水平面的夹角为15~20°。在引流板开有氢气口,氢气口位于引流板斜面的最高处。电解反应器壳体的一侧开有液体产物排出口和氧气排出口,所述电解反应器壳体的一侧为与引流板的斜面最低位置相同的一侧,液体产物排出口紧贴引流板上斜面,氧气排出口紧贴引流板下斜面。The structure of the electrolytic reactor is: the electrolytic reactor housing is cylindrical, the outer diameter of the electrolytic reactor housing is equal to the outer diameter of the tower body housing, and the ratio of the height of the electrolytic reactor housing to the outer diameter is 1.1: 1~1.3︰1. The uppermost end of the electrolytic reactor shell is provided with a drainage plate, which is set on an inclined plane, and the included angle between the drainage plate and the horizontal plane is 15-20°. There is a hydrogen port on the diversion plate, and the hydrogen port is located at the highest point of the slope of the diversion plate. One side of the electrolytic reactor shell is provided with a liquid product discharge port and an oxygen discharge port, and one side of the electrolytic reactor shell is the same side as the lowest position of the slope of the drain plate, and the liquid product discharge port is close to the drain plate On the upper slope, the oxygen outlet is close to the lower slope of the drainage plate.
电解反应器壳体内设有电解反应室,电解反应室位于电解反应器壳体的下部,在电解反应器壳体的底部与电解反应室的底部之间开有进液口。电解反应室为箱体状,箱体顶板、箱体底板、箱体前侧板和箱体后侧板的内壁均匀地开有11个或15个或19个插槽,每个插槽呈“口”字状,每个插槽所在的平面与箱体的左侧板平行。在顺序号为偶数的插槽中均嵌有质子膜,顺序号为1、5、9的插槽中嵌入阳极板(14),或顺序号为1、5、9、13的插槽中嵌入阳极板(14),或顺序号为1、5、9、13、17的插槽中嵌入阳极板,其余插槽均嵌有阴极板。箱体底板和箱体顶板的插槽间均匀地开有一排小孔,每排小孔为12~30个,小孔孔径为5~8mm。箱体顶板的上平面固定有3~5个条形槽板,固定时每个条形槽板的槽口朝下,阴极板两侧的气孔位于条形槽板的槽口内。条形槽板间相通,氢气管道的一端与条形槽板相通,氢气管道的另一端与氢气口相通。An electrolytic reaction chamber is arranged inside the electrolytic reactor shell, and the electrolytic reaction chamber is located at the lower part of the electrolytic reactor shell, and a liquid inlet is opened between the bottom of the electrolytic reactor shell and the bottom of the electrolytic reaction chamber. The electrolytic reaction chamber is in the shape of a box, and there are 11 or 15 or 19 slots evenly opened on the inner wall of the box top plate, box bottom plate, box front side plate and box rear side plate, and each slot is in the shape of " "mouth", the plane where each slot is located is parallel to the left side panel of the cabinet. The proton membranes are embedded in the even-numbered slots, the anode plate (14) is embedded in the slots with the sequence numbers 1, 5, and 9, or the anode plate (14) is embedded in the slots with the sequence numbers 1, 5, 9, and 13 Anode plates (14), or slots with sequence numbers 1, 5, 9, 13 and 17 are embedded with anode plates, and the remaining slots are all embedded with cathode plates. There is a row of small holes evenly opened between the slots of the bottom plate of the cabinet and the top plate of the cabinet, each row of small holes is 12~30, and the diameter of the small holes is 5~8mm. The upper plane of the top plate of the box body is fixed with 3 to 5 strip-shaped slot plates. When fixing, the notch of each strip-shaped slot plate faces downward, and the air holes on both sides of the cathode plate are located in the slots of the strip-shaped slot plate. The strip slots communicate with each other, one end of the hydrogen pipeline communicates with the strip slots, and the other end of the hydrogen pipeline communicates with the hydrogen port.
所述阳极板通过正极导线与电池的正极连接,所述阴极板通过负极导线与电池的负极连接。The anode plate is connected to the positive pole of the battery through the positive pole lead, and the cathode plate is connected to the negative pole of the battery through the negative pole lead.
所述挡板的厚度为1~3cm,挡板的外径与塔身壳体的内径相等;挡板开有小孔,所述小孔的孔径为1~3mm,开孔率为45~65%;所述挡板与上承接板、中承接板和下承接板相同。The thickness of the baffle is 1~3cm, and the outer diameter of the baffle is equal to the inner diameter of the tower shell; %; The baffle plate is the same as the upper receiving plate, the middle receiving plate and the lower receiving plate.
所述第一脱硫脱硝催化剂填料层的填料为活性炭、Cu/Mg/Al催化剂、CuO/Al2O3催化剂和CoMo/Al2O3催化剂中的一种以上,粒径为4~6mm。The filler of the first desulfurization and denitration catalyst filler layer is at least one of activated carbon, Cu/Mg/Al catalyst, CuO/Al 2 O 3 catalyst and CoMo/Al 2 O 3 catalyst, with a particle size of 4-6 mm.
所述固碳催化剂填料层的填料为Cu/Al2O3催化剂和CuO/ZnO/Al2O3催化剂中的一种或两种,粒径为4~6mm。The filler of the carbon-fixing catalyst filler layer is one or both of Cu/Al 2 O 3 catalyst and CuO/ZnO/Al 2 O 3 catalyst, with a particle size of 4-6 mm.
所述第二脱硫脱硝催化剂填料层的填料为活性炭、Cu/Mg/Al催化剂、CuO/Al2O3催化剂和CoMo/Al2O3催化剂中的一种以上,粒径为4~6mm。The filler of the second desulfurization and denitration catalyst filler layer is at least one of activated carbon, Cu/Mg/Al catalyst, CuO/Al 2 O 3 catalyst and CoMo/Al 2 O 3 catalyst, with a particle size of 4-6 mm.
所述固液分离器由不锈钢圈和过滤网布组成,不锈钢圈呈椭圆形,过滤网布固定在不锈钢圈上,过滤网布的材质为聚丙烯或尼龙,孔径为0.045~0.15mm。The solid-liquid separator is composed of a stainless steel ring and a filter cloth, the stainless steel ring is oval, the filter cloth is fixed on the stainless steel ring, the material of the filter cloth is polypropylene or nylon, and the aperture is 0.045~0.15mm.
所述烟气分散器的厚度为5~15cm,烟气分散器开有小孔,所述小孔的孔径为1~5mm,开孔率为30~50%。The thickness of the smoke diffuser is 5-15 cm, and the smoke diffuser is provided with small holes, the diameter of which is 1-5 mm, and the opening ratio is 30-50%.
所述氢气分散器的厚度为5~15cm,氢气分散器开有小孔,所述小孔的孔径为3~5mm,开孔率为50~70%。The thickness of the hydrogen disperser is 5-15 cm, and the hydrogen disperser has small holes, the diameter of the small holes is 3-5 mm, and the opening ratio is 50-70%.
所述质子膜的材料为纳米碳纤维材料。The material of the proton membrane is carbon nanofiber material.
所述条形槽板的两端封闭。Both ends of the strip groove plate are closed.
本装置能对混合烟气中的SO2、NOX和CO2进行净化,还能对产物中的硫磺和甲醇资源回收利用。其具体步骤如下:The device can purify SO 2 , NO X and CO 2 in the mixed flue gas, and can also recycle the sulfur and methanol resources in the product. The specific steps are as follows:
步骤一,通过本装置的进液口,先将水泵入电解反应器中,电解反应器中的电压为2.2V~3.5V,再开启氧气排出口的阀门和氢气口的阀门。电解反应开始,水在电场作用下,分解出H+和OH-,OH-在阳极发生氧化反应生成O2,O2通过阳极板两侧的小孔从电解反应室进入到电解反应器壳体,再通过氧气排出口排出;H+则由阳极穿过质子膜迁移到阴极发生还原反应,与电子结合生成H2,H2通过阴极板两侧的小孔进入条形槽板内,再经过氢气管道通过氢气分散器进入催化反应吸收塔。Step 1: First pump water into the electrolysis reactor through the liquid inlet of the device, the voltage in the electrolysis reactor is 2.2V-3.5V, and then open the valve of the oxygen outlet and the valve of the hydrogen outlet. When the electrolysis reaction starts, water decomposes into H + and OH - under the action of an electric field, and OH - undergoes an oxidation reaction at the anode to generate O 2 , and O 2 enters the electrolysis reactor shell from the electrolysis reaction chamber through the small holes on both sides of the anode plate , and then discharged through the oxygen outlet; H + migrates from the anode through the proton membrane to the cathode for reduction reaction, and combines with electrons to generate H 2 , H 2 enters the strip slot plate through the small holes on both sides of the cathode plate, and then passes through The hydrogen pipeline enters the catalytic reaction absorption tower through the hydrogen disperser.
步骤二,当H2进入催化反应吸收塔时,开启烟气进气口的阀门,通过阀门调节烟气的进气浓度,将经过脱氧预处理后的烟气送入催化反应吸收塔中。脱氧预处理后的烟气经过烟气分散器分散后依次通过第二脱硫脱硝催化剂填料层、固碳催化剂填料层和第一脱硫脱硝催化剂填料层,使其和各个填料层中的催化剂充分接触,进行脱硫、脱硝和固碳反应,得到硫磺、氮气和甲醇。Step 2: When H2 enters the catalytic reaction absorption tower, open the valve of the flue gas inlet, adjust the intake concentration of the flue gas through the valve, and send the flue gas after deoxygenation pretreatment into the catalytic reaction absorption tower. The flue gas after the deoxidation pretreatment is dispersed through the flue gas disperser, and then passes through the second desulfurization and denitration catalyst packing layer, the carbon fixation catalyst packing layer and the first desulfurization and denitration catalyst packing layer, so that it can fully contact with the catalyst in each packing layer, Desulfurization, denitrification and carbon fixation reactions are carried out to obtain sulfur, nitrogen and methanol.
步骤三,对烟气净化后的产物进行收集处理。脱硝反应产生的氮气通过排气口排出;脱硫反应生成的硫磺滞留在固液分离器的过滤网布上,由固体产物排出口排出收集;固碳反应生成的甲醇通过液体产物排出口收集作为燃料利用。Step 3, collecting and processing the products after flue gas purification. The nitrogen generated by the denitrification reaction is discharged through the exhaust port; the sulfur generated by the desulfurization reaction is retained on the filter cloth of the solid-liquid separator, and is discharged and collected from the solid product discharge port; the methanol generated by the carbon fixation reaction is collected through the liquid product discharge port as fuel use.
由于采用上述技术方案,本发明与现有技术相比具有以下积极效果:Owing to adopting above-mentioned technical scheme, the present invention has following positive effect compared with prior art:
1.本装置采用了质子膜电解水制氢技术,能提供充足的还原性气体-氢气,降低了投资和运行费用。1. This device adopts the proton membrane electrolysis water hydrogen production technology, which can provide sufficient reducing gas-hydrogen, and reduces investment and operating costs.
2.本装置在烟气进气口设置有烟气分散器,在氢气口设置有氢气分散器,大大增加了烟气与氢气和催化剂的接触面积,烟气净化效率高。2. The device is equipped with a flue gas diffuser at the flue gas inlet, and a hydrogen gas diffuser at the hydrogen gas port, which greatly increases the contact area between flue gas, hydrogen and catalyst, and has high flue gas purification efficiency.
3.本装置通过使用多重催化剂,在吸收烟气SO2、NOX以及CO2的同时,将烟气转化为硫磺和甲醇,转化效率达到95%,产物回收再利用效果好。3. This device uses multiple catalysts to convert flue gas into sulfur and methanol while absorbing flue gas SO 2 , NO X and CO 2 . The conversion efficiency reaches 95%, and the product recovery and reuse effect is good.
4.本装置实现了混合烟气的一体化催化吸收反应,集脱硫、脱硝与固碳反应为一体,占地面积小,结构简单,为工业烟气处理提供了方便。4. This device realizes the integrated catalytic absorption reaction of mixed flue gas, integrates desulfurization, denitration and carbon fixation reactions, occupies a small area, and has a simple structure, which provides convenience for industrial flue gas treatment.
因此,本装置具有结构简单、占地面积小、投资和运行费用低、烟气净化效率高和产物回收再利用效果好的特点。Therefore, the device has the characteristics of simple structure, small floor space, low investment and operation costs, high flue gas purification efficiency and good product recovery and reuse effect.
附图说明Description of drawings
图1为本发明的一种结构示意图;Fig. 1 is a kind of structural representation of the present invention;
图2为图1的A-A向放大示意图;Figure 2 is an enlarged schematic diagram of the A-A direction of Figure 1;
图3为图1和图2中条形槽板(19)的截面放大示意图。Fig. 3 is an enlarged cross-sectional schematic diagram of the strip groove plate (19) in Fig. 1 and Fig. 2 .
具体实施方式detailed description
下面结合附图和具体实施方式对本发明作进一步详细的说明,并非对其保护范围的限制。The present invention will be described in further detail below in conjunction with the accompanying drawings and specific embodiments, without limiting its protection scope.
实施例1Example 1
一种质子膜电催化烟气脱硫脱硝装置。如图1所示,所述装置由催化反应吸收塔和电解反应器组成,催化反应吸收塔的下端和电解反应器的上端同中心线连接为整体。A proton membrane electrocatalytic flue gas desulfurization and denitrification device. As shown in Figure 1, the device is composed of a catalytic reaction absorption tower and an electrolytic reactor, the lower end of the catalytic reaction absorption tower and the upper end of the electrolytic reactor are connected as a whole with the central line.
催化反应吸收塔的结构如图1所示:顶盖29和塔身5通过法兰同中心线固定连接,顶盖29的纵截面呈圆弧状,顶盖29的中心位置处设有排气口1。The structure of the catalytic reaction absorption tower is shown in Figure 1: the top cover 29 and the tower body 5 are fixedly connected with the center line through flanges, the longitudinal section of the top cover 29 is arc-shaped, and the center of the top cover 29 is provided with an exhaust port 1.
塔身5的结构如图1所示:塔身壳体27为空心圆柱体,塔身壳体27的高度和外径比为3︰1~4︰1。在塔身壳体27内,从上端到靠近下端处依次设有挡板28、第一脱硫脱硝催化剂填料层2、上承接板26、固碳催化剂填料层3、中承接板25、第二脱硫脱硝催化剂填料层4、下承接板24、固液分离器23、烟气分散器6和氢气分散器7。The structure of the tower body 5 is shown in FIG. 1 : the tower body shell 27 is a hollow cylinder, and the ratio of the height to the outer diameter of the tower body shell 27 is 3:1~4:1. Inside the tower shell 27, there are baffles 28, a first desulfurization and denitrification catalyst packing layer 2, an upper receiving plate 26, a carbon-fixing catalyst packing layer 3, a middle receiving plate 25, and a second desulfurization Denitration catalyst packing layer 4 , lower receiving plate 24 , solid-liquid separator 23 , flue gas diffuser 6 and hydrogen gas diffuser 7 .
其中:挡板28与上承接板26间的距离、上承接板26与中承接板25间的距离和中承接板25与下承接板24间的距离相等,第一脱硫脱硝催化剂填料层2、固碳催化剂填料层3和第二脱硫脱硝催化剂填料层4的填料填充率为0.9~1倍。固液分离器23为斜面设置,固液分离器23与水平面的夹角为15~20°,固液分离器23与塔身壳体27的内壁固定连接。塔身壳体27的一侧开有固体产物排出口22,所述塔身壳体27的一侧为与固液分离器23的斜面最低位置相同的一侧,固体产物排出口22紧贴固液分离器23的上斜面。在塔身壳体27的另一侧开有烟气进气口8,烟气进气口8位于烟气分散器6和氢气分散器7之间。烟气分散器6的上平面到下承接板24的下平面间的距离为塔身壳体27内径的0.3~0.4倍,氢气分散器7的上平面到烟气分散器6的下平面间的距离为塔身壳体27内径的0.2~0.3倍。Wherein: the distance between the baffle plate 28 and the upper receiving plate 26, the distance between the upper receiving plate 26 and the middle receiving plate 25 and the distance between the middle receiving plate 25 and the lower receiving plate 24 are equal, the first desulfurization and denitrification catalyst packing layer 2, The filler filling rate of the carbon-fixing catalyst packing layer 3 and the second desulfurization and denitrification catalyst packing layer 4 is 0.9 to 1 times. The solid-liquid separator 23 is arranged on a slope, the angle between the solid-liquid separator 23 and the horizontal plane is 15-20°, and the solid-liquid separator 23 is fixedly connected to the inner wall of the tower shell 27 . One side of the tower body shell 27 has a solid product discharge port 22, and one side of the tower body shell 27 is the same side as the lowest position of the slope of the solid-liquid separator 23, and the solid product discharge port 22 is close to the solid The upper slope of the liquid separator 23. A flue gas inlet 8 is opened on the other side of the tower shell 27 , and the flue gas inlet 8 is located between the flue gas diffuser 6 and the hydrogen diffuser 7 . The distance between the upper plane of the flue gas diffuser 6 and the lower plane of the lower receiving plate 24 is 0.3 to 0.4 times the inner diameter of the tower shell 27, and the distance between the upper plane of the hydrogen diffuser 7 and the lower plane of the flue gas diffuser 6 The distance is 0.2 to 0.3 times the inner diameter of the tower shell 27 .
所述电解反应器的结构如图1所示:电解反应器壳体18为圆筒状,电解反应器壳体18外径与塔身壳体27的外径相等,电解反应器壳体18的高度与外径之比为1.1︰1~1.2︰1。电解反应器壳体18最上端设有引流板10,引流板10为斜面设置,引流板10与水平面的夹角为15~20°。在引流板10开有氢气口9,氢气口9位于引流板10斜面的最高处。电解反应器壳体18的一侧开有液体产物排出口21和氧气排出口20,所述电解反应器壳体18的一侧为与引流板10的斜面最低位置相同的一侧,液体产物排出口21紧贴引流板10上斜面,氧气排出口20紧贴引流板10下斜面。The structure of the electrolytic reactor is as shown in Figure 1: the electrolytic reactor housing 18 is cylindrical, and the outer diameter of the electrolytic reactor housing 18 is equal to the outer diameter of the tower body housing 27, and the outer diameter of the electrolytic reactor housing 18 The ratio of height to outer diameter is 1.1︰1~1.2︰1. The uppermost end of the electrolytic reactor shell 18 is provided with a diversion plate 10, which is arranged on an inclined plane, and the included angle between the diversion plate 10 and the horizontal plane is 15-20°. A hydrogen port 9 is opened on the diversion plate 10 , and the hydrogen port 9 is located at the highest point of the slope of the diversion plate 10 . One side of the electrolytic reactor housing 18 has a liquid product discharge port 21 and an oxygen discharge port 20, and one side of the electrolytic reactor housing 18 is the same side as the lowest position of the slope of the drain plate 10, and the liquid product discharge port The outlet 21 is close to the upper slope of the drainage plate 10 , and the oxygen outlet 20 is close to the lower slope of the drainage plate 10 .
如图1所示,电解反应器壳体18内设有电解反应室,电解反应室位于电解反应器壳体18的下部,在电解反应器壳体18的底部与电解反应室的底部之间开有进液口16。电解反应室为箱体状,箱体顶板、箱体底板、箱体前侧板和箱体后侧板的内壁均匀地开有11个插槽,每个插槽呈“口”字状,每个插槽所在的平面与箱体的左侧板平行。在顺序号为偶数的插槽中均嵌有质子膜13,顺序号为1、5、9的插槽中嵌入阳极板14,其余插槽均嵌有阴极板12。箱体底板和箱体顶板的插槽间均匀地开有一排小孔,每排小孔为12个,小孔孔径为8mm。如图1和图2所示,箱体顶板的上平面固定有3个条形槽板19;如图3所示,固定时每个条形槽板19的槽口朝下,所述条形槽板19的两端封闭。如图1和图2所示,阴极板12两侧的气孔位于条形槽板19的槽口内。条形槽板19间相通,氢气管道11的一端与条形槽板19相通,氢气管道11的另一端与氢气口9相通。As shown in Figure 1, electrolytic reaction chamber is provided with electrolytic reaction chamber in the electrolytic reactor housing 18, and electrolytic reaction chamber is positioned at the bottom of electrolytic reactor housing 18, opens between the bottom of electrolytic reactor housing 18 and the bottom of electrolytic reaction chamber. Liquid inlet 16 is arranged. The electrolytic reaction chamber is in the shape of a box, and 11 slots are evenly opened on the inner wall of the box top, box bottom, box front side plate and box rear side plate, and each slot is in the shape of a "mouth". The plane where the two slots are located is parallel to the left side panel of the cabinet. Proton membranes 13 are embedded in slots with even numbers, anode plates 14 are embedded in slots with sequence numbers 1, 5, and 9, and cathode plates 12 are embedded in the remaining slots. A row of small holes is evenly opened between the slots on the bottom plate of the box body and the top plate of the box body. There are 12 small holes in each row, and the diameter of the small holes is 8mm. As shown in Figures 1 and 2, three strip-shaped groove plates 19 are fixed on the upper plane of the top plate of the box body; The two ends of slot plate 19 are closed. As shown in FIG. 1 and FIG. 2 , the air holes on both sides of the cathode plate 12 are located in the notch of the strip-shaped slot plate 19 . The strip slots 19 communicate with each other, one end of the hydrogen pipeline 11 communicates with the strip slot 19 , and the other end of the hydrogen pipeline 11 communicates with the hydrogen port 9 .
所述阳极板14通过正极导线17与电池的正极连接,所述阴极板12通过负极导线15与电池的负极连接。The anode plate 14 is connected to the positive pole of the battery through the positive pole lead 17 , and the cathode plate 12 is connected to the negative pole of the battery through the negative pole lead 15 .
所述挡板28的厚度为1~3cm,挡板28的外径与塔身壳体27的内径相等;挡板28开有小孔,所述小孔的孔径为1~3mm,开孔率为45~65%;所述挡板28与上承接板26、中承接板25和下承接板24相同。The thickness of described baffle plate 28 is 1~3cm, and the outer diameter of baffle plate 28 is equal to the inner diameter of tower body shell 27; 45~65%; the baffle plate 28 is the same as the upper receiving plate 26, the middle receiving plate 25 and the lower receiving plate 24.
所述第一脱硫脱硝催化剂填料层2的填料为活性炭、Cu/Mg/Al催化剂、CuO/Al2O3催化剂和CoMo/Al2O3催化剂中的一种以上,粒径为4~6mm。The filler of the first desulfurization and denitration catalyst filler layer 2 is at least one of activated carbon, Cu/Mg/Al catalyst, CuO/Al 2 O 3 catalyst and CoMo/Al 2 O 3 catalyst, with a particle size of 4-6 mm.
所述固碳催化剂填料层3的填料为Cu/Al2O3催化剂和CuO/ZnO/Al2O3催化剂中的一种或两种,粒径为4~6mm。The filler of the carbon-fixing catalyst filler layer 3 is one or both of Cu/Al 2 O 3 catalyst and CuO/ZnO/Al 2 O 3 catalyst, with a particle size of 4-6 mm.
所述第二脱硫脱硝催化剂填料层4的填料为活性炭、Cu/Mg/Al催化剂、CuO/Al2O3催化剂和CoMo/Al2O3催化剂中的一种以上,粒径为4~6mm。The filler of the second desulfurization and denitration catalyst filler layer 4 is at least one of activated carbon, Cu/Mg/Al catalyst, CuO/Al 2 O 3 catalyst and CoMo/Al 2 O 3 catalyst, with a particle size of 4-6 mm.
所述固液分离器23由不锈钢圈和过滤网布组成,不锈钢圈呈椭圆形,过滤网布固定在不锈钢圈上,过滤网布的材质为聚丙烯或尼龙,孔径为0.045~0.15mm。The solid-liquid separator 23 is composed of a stainless steel ring and a filter cloth, the stainless steel ring is oval, the filter cloth is fixed on the stainless steel ring, the material of the filter cloth is polypropylene or nylon, and the aperture is 0.045-0.15mm.
所述烟气分散器6的厚度为5~15cm,烟气分散器6开有小孔,所述小孔的孔径为1~5mm,开孔率为30~50%。The thickness of the smoke diffuser 6 is 5-15 cm, and the smoke diffuser 6 has small holes, the diameter of which is 1-5 mm, and the opening ratio is 30-50%.
所述氢气分散器7的厚度为5~15cm,氢气分散器7开有小孔,所述小孔的孔径为3~5mm,开孔率为50~70%。The thickness of the hydrogen diffuser 7 is 5-15 cm, and the hydrogen diffuser 7 has small holes, the diameter of the small holes is 3-5 mm, and the opening ratio is 50-70%.
所述质子膜13的材料为纳米碳纤维材料。The material of the proton membrane 13 is carbon nanofiber material.
实施例2Example 2
一种质子膜电催化烟气脱硫脱硝装置。除下述技术参数外其余同实施例1:A proton membrane electrocatalytic flue gas desulfurization and denitrification device. Except following technical parameter, all the other are with embodiment 1:
塔身壳体27的高度和外径比为4︰1~5︰1。The height and outer diameter ratio of the tower shell 27 is 4:1~5:1.
电解反应器壳体18的高度与外径之比为1.2︰1~1.3︰1。The ratio of the height to the outer diameter of the electrolytic reactor shell 18 is 1.2:1~1.3:1.
电解反应室为箱体状,箱体顶板、箱体底板、箱体前侧板和箱体后侧板的内壁均匀地开有15个插槽,每个插槽呈“口”字状,每个插槽所在的平面与箱体的左侧板平行。在顺序号为偶数的插槽中均嵌有质子膜13,顺序号为1、5、9、13的插槽中嵌入阳极板(14),其余插槽均嵌有阴极板12。箱体底板和箱体顶板的插槽间均匀地开有一排小孔,每排小孔为13~30个,小孔孔径为5~8mm。箱体顶板的上平面设有4个条形槽板19。The electrolytic reaction chamber is in the shape of a box, and there are 15 slots uniformly opened on the inner wall of the top plate, bottom plate, front side plate and rear side plate of the box body, and each slot is in the shape of a “mouth”. The plane where the two slots are located is parallel to the left side panel of the cabinet. Proton membranes 13 are embedded in slots with even numbers, anode plates (14) are embedded in slots with sequence numbers 1, 5, 9 and 13, and cathode plates 12 are embedded in the remaining slots. A row of small holes is evenly opened between the slots on the bottom plate of the cabinet and the top plate of the cabinet, each row of small holes is 13~30, and the diameter of the small holes is 5~8mm. The upper plane of the top plate of the box body is provided with 4 strip groove plates 19 .
实施例3Example 3
一种质子膜电催化烟气脱硫脱硝装置。除下述技术参数外其余同实施例2:A proton membrane electrocatalytic flue gas desulfurization and denitrification device. Except following technical parameter, all the other are with embodiment 2:
电解反应室为箱体状,箱体顶板、箱体底板、箱体前侧板和箱体后侧板的内壁均匀地开有19个插槽,每个插槽呈“口”字状,每个插槽所在的平面与箱体的左侧板平行。在顺序号为偶数的插槽中均嵌有质子膜13,顺序号为1、5、9、13、17的插槽中嵌入阳极板14,其余插槽均嵌有阴极板12。箱体顶板的上平面设有5个条形槽板19。The electrolytic reaction chamber is in the shape of a box. There are 19 slots evenly opened on the inner wall of the box top, box bottom, box front side plate and box rear side plate. Each slot is in the shape of a "mouth". The plane where the two slots are located is parallel to the left side panel of the cabinet. Proton membranes 13 are embedded in slots with even numbers, anode plates 14 are embedded in slots with sequence numbers 1, 5, 9, 13 and 17, and cathode plates 12 are embedded in the remaining slots. The upper plane of the top plate of the box body is provided with 5 strip groove plates 19 .
本装置能对混合烟气中的SO2、NOX和CO2进行净化,还能对产物中的硫磺和甲醇资源回收利用。其具体步骤如下:The device can purify SO 2 , NO X and CO 2 in the mixed flue gas, and can also recycle the sulfur and methanol resources in the product. The specific steps are as follows:
步骤一,通过本装置的进液口16,先将水泵入电解反应器中,电解反应器中的电压为2.2V~3.5V,再开启氧气排出口20的阀门和氢气口9的阀门。电解反应开始,水在电场作用下,分解出H+和OH-,OH-在阳极发生氧化反应生成O2,O2通过阳极板14两侧的小孔从电解反应室进入到电解反应器壳体18,再通过氧气排出口20排出;H+则由阳极穿过质子膜13迁移到阴极发生还原反应,与电子结合生成H2,H2通过阴极板12两侧的小孔进入条形槽板19内,再经过氢气管道11通过氢气分散器7进入催化反应吸收塔。Step 1: First pump water into the electrolysis reactor through the liquid inlet 16 of the device, the voltage in the electrolysis reactor is 2.2V-3.5V, and then open the valve of the oxygen outlet 20 and the valve of the hydrogen outlet 9. When the electrolysis reaction starts, water decomposes into H + and OH - under the action of an electric field, and OH - undergoes an oxidation reaction at the anode to generate O 2 , and O 2 enters the electrolysis reactor shell from the electrolysis reaction chamber through the small holes on both sides of the anode plate 14 body 18, and then discharged through the oxygen discharge port 20; H + will migrate from the anode through the proton membrane 13 to the cathode to undergo a reduction reaction, and combine with electrons to generate H 2 , and H 2 enters the strip groove through the small holes on both sides of the cathode plate 12 In the plate 19, it enters the catalytic reaction absorption tower through the hydrogen gas disperser 7 through the hydrogen gas pipeline 11.
步骤二,当H2进入催化反应吸收塔时,开启烟气进气口8的阀门,通过阀门调节烟气的进气浓度,将经过脱氧预处理后的烟气送入催化反应吸收塔中。脱氧预处理后的烟气经过烟气分散器6分散后依次通过第二脱硫脱硝催化剂填料层4、固碳催化剂填料层3和第一脱硫脱硝催化剂填料层2,使其和各个填料层中的催化剂充分接触,进行脱硫、脱硝和固碳反应,得到硫磺、氮气和甲醇。Step 2, when H2 enters the catalytic reaction absorption tower, open the valve of the flue gas inlet 8, adjust the intake concentration of the flue gas through the valve, and send the flue gas after deoxidation pretreatment into the catalytic reaction absorption tower. The flue gas after the deoxidation pretreatment is dispersed through the flue gas disperser 6 and then passes through the second desulfurization and denitration catalyst packing layer 4, the carbon fixation catalyst packing layer 3 and the first desulfurization and denitration catalyst packing layer 2, so that it can be mixed with the The catalysts are fully contacted to perform desulfurization, denitrification and carbon fixation reactions to obtain sulfur, nitrogen and methanol.
步骤三,对烟气净化后的产物进行收集处理。脱硝反应产生的氮气通过排气口1排出;脱硫反应生成的硫磺滞留在固液分离器23的过滤网布上,由固体产物排出口22排出收集;固碳反应生成的甲醇通过液体产物排出口21收集作为燃料利用。Step 3, collecting and processing the products after flue gas purification. The nitrogen generated by the denitrification reaction is discharged through the exhaust port 1; the sulfur generated by the desulfurization reaction stays on the filter cloth of the solid-liquid separator 23, and is discharged and collected from the solid product discharge port 22; the methanol generated by the carbon fixation reaction passes through the liquid product discharge port 21 collected as fuel utilization.
本具体实施方式与现有技术相比具有以下积极效果:Compared with the prior art, this specific embodiment has the following positive effects:
1.本装置采用了质子膜电解水制氢技术,能提供充足的还原性气体-氢气,降低了投资和运行费用。1. This device adopts the proton membrane electrolysis water hydrogen production technology, which can provide sufficient reducing gas-hydrogen, and reduces investment and operating costs.
2.本装置在烟气进气口8设置有烟气分散器6,在氢气口9设置有氢气分散器7,大大增加了烟气与氢气和催化剂的接触面积,烟气净化效率高。2. The device is equipped with a flue gas diffuser 6 at the flue gas inlet 8, and a hydrogen gas diffuser 7 at the hydrogen gas port 9, which greatly increases the contact area between flue gas, hydrogen and catalyst, and has high flue gas purification efficiency.
3.本装置通过使用多重催化剂,在吸收烟气SO2、NOX以及CO2的同时,将烟气转化为硫磺和甲醇,转化效率达到95%,产物回收再利用效果好。3. This device uses multiple catalysts to convert flue gas into sulfur and methanol while absorbing flue gas SO 2 , NO X and CO 2 . The conversion efficiency reaches 95%, and the product recovery and reuse effect is good.
4.本装置实现了混合烟气的一体化催化吸收反应,集脱硫、脱硝与固碳反应为一体,占地面积小,结构简单,为工业烟气处理提供了方便。4. This device realizes the integrated catalytic absorption reaction of mixed flue gas, integrates desulfurization, denitration and carbon fixation reactions, occupies a small area, and has a simple structure, which provides convenience for industrial flue gas treatment.
因此,本装置具有结构简单、占地面积小、投资和运行费用低、烟气净化效率高和产物回收再利用效果好的特点。Therefore, the device has the characteristics of simple structure, small floor space, low investment and operation costs, high flue gas purification efficiency and good product recovery and reuse effect.
Claims (10)
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN201510580979.9A CN105107374B (en) | 2015-09-14 | 2015-09-14 | Flue gas desulfurization and denitration device utilizing proton membrane electrocatalysis |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN201510580979.9A CN105107374B (en) | 2015-09-14 | 2015-09-14 | Flue gas desulfurization and denitration device utilizing proton membrane electrocatalysis |
Publications (2)
Publication Number | Publication Date |
---|---|
CN105107374A CN105107374A (en) | 2015-12-02 |
CN105107374B true CN105107374B (en) | 2017-03-22 |
Family
ID=54655617
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
CN201510580979.9A Expired - Fee Related CN105107374B (en) | 2015-09-14 | 2015-09-14 | Flue gas desulfurization and denitration device utilizing proton membrane electrocatalysis |
Country Status (1)
Country | Link |
---|---|
CN (1) | CN105107374B (en) |
Families Citing this family (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN109289465A (en) * | 2018-09-17 | 2019-02-01 | 中国神华能源股份有限公司 | Oxygen-enriched combusting flue gas concerted catalysis method and device |
CN109482025A (en) * | 2018-12-18 | 2019-03-19 | 王亚威 | A kind of harmful organic soot processing device of industry |
Citations (5)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN1687637A (en) * | 2005-05-30 | 2005-10-26 | 史汉祥 | Technique of non-pollutant discharge for comprehensive treating coal-burning boiler |
CN202460474U (en) * | 2012-01-19 | 2012-10-03 | 大连贝斯特环境工程设备有限公司 | Integral desulfurization and denitration complete device by catalytic reduction ammonia method for small and medium boilers |
CN102884292A (en) * | 2010-04-02 | 2013-01-16 | 俄亥俄州立大学 | Selective catalytic reduction via electrolysis of urea |
CN104722177A (en) * | 2015-02-04 | 2015-06-24 | 中国华能集团清洁能源技术研究院有限公司 | Carbon dioxide capturing system for concentration conversion and electrolysis regeneration |
CN205055781U (en) * | 2015-09-14 | 2016-03-02 | 武汉科技大学 | Catalysis flue gas desulfurization denitrification facility is reinforceed to electrochemistry proton membrane |
Family Cites Families (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
US8821818B1 (en) * | 2013-03-15 | 2014-09-02 | Three D Stack, LLC | Cleaning stack gas |
-
2015
- 2015-09-14 CN CN201510580979.9A patent/CN105107374B/en not_active Expired - Fee Related
Patent Citations (5)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN1687637A (en) * | 2005-05-30 | 2005-10-26 | 史汉祥 | Technique of non-pollutant discharge for comprehensive treating coal-burning boiler |
CN102884292A (en) * | 2010-04-02 | 2013-01-16 | 俄亥俄州立大学 | Selective catalytic reduction via electrolysis of urea |
CN202460474U (en) * | 2012-01-19 | 2012-10-03 | 大连贝斯特环境工程设备有限公司 | Integral desulfurization and denitration complete device by catalytic reduction ammonia method for small and medium boilers |
CN104722177A (en) * | 2015-02-04 | 2015-06-24 | 中国华能集团清洁能源技术研究院有限公司 | Carbon dioxide capturing system for concentration conversion and electrolysis regeneration |
CN205055781U (en) * | 2015-09-14 | 2016-03-02 | 武汉科技大学 | Catalysis flue gas desulfurization denitrification facility is reinforceed to electrochemistry proton membrane |
Also Published As
Publication number | Publication date |
---|---|
CN105107374A (en) | 2015-12-02 |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
CN202497818U (en) | Multi-level comprehensive treatment system for foul gas | |
CN103830986A (en) | Integrated dust removal-purification device and purification method of stationary diesel engine system | |
CN210544365U (en) | A reactant removes bed for flue gas desulfurization denitration treatment system | |
KR102430685B1 (en) | High concentration hydrogen sulfide removal device in solution bath type | |
CN105107374B (en) | Flue gas desulfurization and denitration device utilizing proton membrane electrocatalysis | |
CN100421769C (en) | Method for unwanted exhaust gas purification and dedicated apparatus | |
CN101804294B (en) | Method and device for treating pollutant and dust in gas | |
CN205055781U (en) | Catalysis flue gas desulfurization denitrification facility is reinforceed to electrochemistry proton membrane | |
CN107890758B (en) | External circulation type electrochemical sewage treatment plant deodorization system and method | |
CN206273334U (en) | A kind of sewage plant process stink collection and cleaning treatment system | |
CN204841388U (en) | Box VOC decomposes compound purification unit | |
CN104556565B (en) | An anaerobic reactor for in-situ electrochemical reduction of CO2 products | |
CN214680883U (en) | Organic waste gas treatment and purification equipment | |
CN204447762U (en) | The absorption tower that a kind of reduction efficiency is high | |
ITRM20130367A1 (en) | GROUP FOR THE PRODUCTION OF GAS METHANE ISSUED BY THE SOIL | |
CN211635954U (en) | Effluent water sump adds lid tail gas purification deodorizing device | |
CN209721886U (en) | An energy-saving catalytic water treatment device with power generation of 20-87W/m2 | |
CN203916451U (en) | Waste gas filtering machine | |
CN210620387U (en) | Double-effect nitrogen and phosphorus removal device | |
CN203694875U (en) | Radial cross-flow moving-bed reactor for removal of hydrogen sulfide by temperature swing adsorption | |
CN107185404A (en) | A kind of gas cleaning absorption tower and its flue gas purifying method and application | |
CN207745621U (en) | The tail gas activated carbon adsorption case prepared for H acid monosodium salt | |
CN218358131U (en) | Novel waste gas purification equipment for garbage transfer station | |
CN216799372U (en) | Efficient purification treatment system for biogas power generation tail gas | |
CN204447744U (en) | One way of life Sewage Disposal odor purification equipment |
Legal Events
Date | Code | Title | Description |
---|---|---|---|
C06 | Publication | ||
PB01 | Publication | ||
C10 | Entry into substantive examination | ||
SE01 | Entry into force of request for substantive examination | ||
C14 | Grant of patent or utility model | ||
GR01 | Patent grant | ||
CF01 | Termination of patent right due to non-payment of annual fee |
Granted publication date: 20170322 Termination date: 20170914 |
|
CF01 | Termination of patent right due to non-payment of annual fee |