CN108554150A - A kind of pre-heated catalytic combustion system of purifying volatile organic exhaust gas - Google Patents
A kind of pre-heated catalytic combustion system of purifying volatile organic exhaust gas Download PDFInfo
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- 239000007789 gas Substances 0.000 claims abstract description 99
- 238000001179 sorption measurement Methods 0.000 claims abstract description 64
- 239000012855 volatile organic compound Substances 0.000 claims abstract description 55
- 239000010815 organic waste Substances 0.000 claims abstract description 33
- 239000002912 waste gas Substances 0.000 claims abstract description 24
- 238000003860 storage Methods 0.000 claims abstract description 8
- 230000006835 compression Effects 0.000 claims abstract description 7
- 238000007906 compression Methods 0.000 claims abstract description 7
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 claims description 112
- 230000003197 catalytic effect Effects 0.000 claims description 30
- 239000003054 catalyst Substances 0.000 claims description 27
- 239000007788 liquid Substances 0.000 claims description 20
- 239000007921 spray Substances 0.000 claims description 20
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- 239000002274 desiccant Substances 0.000 claims description 14
- 238000010438 heat treatment Methods 0.000 claims description 9
- 238000001816 cooling Methods 0.000 claims description 8
- 230000001105 regulatory effect Effects 0.000 claims description 8
- AXCZMVOFGPJBDE-UHFFFAOYSA-L calcium dihydroxide Chemical class [OH-].[OH-].[Ca+2] AXCZMVOFGPJBDE-UHFFFAOYSA-L 0.000 claims description 6
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- 150000008282 halocarbons Chemical class 0.000 description 1
- 239000002920 hazardous waste Substances 0.000 description 1
- 150000002430 hydrocarbons Chemical class 0.000 description 1
- 239000013067 intermediate product Substances 0.000 description 1
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- IJGRMHOSHXDMSA-UHFFFAOYSA-N nitrogen Substances N#N IJGRMHOSHXDMSA-UHFFFAOYSA-N 0.000 description 1
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- 150000002894 organic compounds Chemical class 0.000 description 1
- TWNQGVIAIRXVLR-UHFFFAOYSA-N oxo(oxoalumanyloxy)alumane Chemical compound O=[Al]O[Al]=O TWNQGVIAIRXVLR-UHFFFAOYSA-N 0.000 description 1
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Classifications
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D53/00—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
- B01D53/002—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols by condensation
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D53/00—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
- B01D53/02—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols by adsorption, e.g. preparative gas chromatography
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D53/00—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
- B01D53/34—Chemical or biological purification of waste gases
- B01D53/38—Removing components of undefined structure
- B01D53/44—Organic components
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D53/00—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
- B01D53/34—Chemical or biological purification of waste gases
- B01D53/74—General processes for purification of waste gases; Apparatus or devices specially adapted therefor
- B01D53/77—Liquid phase processes
- B01D53/78—Liquid phase processes with gas-liquid contact
-
- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23G—CREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
- F23G7/00—Incinerators or other apparatus for consuming industrial waste, e.g. chemicals
- F23G7/06—Incinerators or other apparatus for consuming industrial waste, e.g. chemicals of waste gases or noxious gases, e.g. exhaust gases
- F23G7/07—Incinerators or other apparatus for consuming industrial waste, e.g. chemicals of waste gases or noxious gases, e.g. exhaust gases in which combustion takes place in the presence of catalytic material
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2251/00—Reactants
- B01D2251/10—Oxidants
- B01D2251/106—Peroxides
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2257/00—Components to be removed
- B01D2257/70—Organic compounds not provided for in groups B01D2257/00 - B01D2257/602
- B01D2257/708—Volatile organic compounds V.O.C.'s
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2259/00—Type of treatment
- B01D2259/40—Further details for adsorption processes and devices
- B01D2259/40083—Regeneration of adsorbents in processes other than pressure or temperature swing adsorption
- B01D2259/40088—Regeneration of adsorbents in processes other than pressure or temperature swing adsorption by heating
- B01D2259/4009—Regeneration of adsorbents in processes other than pressure or temperature swing adsorption by heating using hot gas
-
- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23G—CREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
- F23G2202/00—Combustion
- F23G2202/60—Combustion in a catalytic combustion chamber
-
- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23G—CREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
- F23G2209/00—Specific waste
- F23G2209/14—Gaseous waste or fumes
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- Engineering & Computer Science (AREA)
- Chemical & Material Sciences (AREA)
- Environmental & Geological Engineering (AREA)
- Chemical Kinetics & Catalysis (AREA)
- Analytical Chemistry (AREA)
- General Chemical & Material Sciences (AREA)
- Oil, Petroleum & Natural Gas (AREA)
- Health & Medical Sciences (AREA)
- Biomedical Technology (AREA)
- Mechanical Engineering (AREA)
- General Engineering & Computer Science (AREA)
- Incineration Of Waste (AREA)
- Treating Waste Gases (AREA)
- Exhaust Gas Treatment By Means Of Catalyst (AREA)
Abstract
本发明公开了一种净化挥发性有机废气的预热式催化燃烧系统,其主要涉及废气处理领域,包括依次连通的压缩储存单元、吸附单元和催化燃烧单元,通过三个单元对VOCs废气进行处理,既能够保证净化效率,由能够减少热能的损失,而且也有利于回收有机溶剂,从而大幅度提高了VOCs废气处理的经济效益。
The invention discloses a preheating catalytic combustion system for purifying volatile organic waste gas, which mainly relates to the field of waste gas treatment, including a sequentially connected compression storage unit, an adsorption unit and a catalytic combustion unit, through which VOCs waste gas is processed. , which can not only ensure the purification efficiency, but also reduce the loss of heat energy, and is also conducive to the recovery of organic solvents, thereby greatly improving the economic benefits of VOCs waste gas treatment.
Description
技术领域technical field
本发明涉及领域废气处理领域,更具体地说,它涉及一种净化挥发性有机废气的预热式催化燃烧系统。The invention relates to the field of waste gas treatment, more specifically, it relates to a preheating catalytic combustion system for purifying volatile organic waste gas.
背景技术Background technique
挥发性有机物(Volatileorganiccompounds,VOCs)通常是指在25℃时,饱和蒸汽压大于133Pa的有机化合物,其主要成分为烃类、卤代烃类、氧烃类、硫烃类、氮烃类、芳香烃和多环芳烃。VOCs是一类在石油化工行业、喷涂喷漆行业、油漆涂料生产加工行业、橡胶生产加工行业、印刷印染行业等生产过程中的常用试剂,由此产生的VOCs废气通常具有成分复杂,排放浓度变化大,不易溶于水、含酸或碱的特点而难以处理。Volatile organic compounds (Volatile organic compounds, VOCs) usually refer to organic compounds with a saturated vapor pressure greater than 133Pa at 25°C, and their main components are hydrocarbons, halogenated hydrocarbons, oxygen hydrocarbons, sulfur hydrocarbons, nitrogen hydrocarbons, aromatic hydrocarbons and polycyclic aromatic hydrocarbons. VOCs are a kind of commonly used reagents in the petrochemical industry, spray painting industry, paint production and processing industry, rubber production and processing industry, printing and dyeing industry, etc. The resulting VOCs exhaust gas usually has complex components and large changes in emission concentration. , not easily soluble in water, containing acid or alkali characteristics and difficult to handle.
目前,针对VOCs的常规处理方法有:冷凝法,主要用于回收高浓度、高沸点、小气量的单组分气体,对复杂组分的废气回收率低;吸收法,主要针对大气量、高浓度、溶解性的废气,但对溶解性差的废气处理效率低;活性炭吸附法,适用于低浓度、大气量的VOCs废气,活性炭很容易吸附饱和,更换吸附剂的费用昂贵并且吸附饱和后的活性炭需作为一种危险废物处理;燃烧法,主要针对高浓度、复杂组分的有机废气,该方法工艺简单、去除效率高。而吸附、燃烧结合法,不仅适合处理不同浓度和不同组分的废气,同时,其去除效率高。At present, the conventional treatment methods for VOCs are: condensation method, which is mainly used to recover single-component gases with high concentration, high boiling point and small gas volume, and has a low recovery rate of exhaust gas from complex components; absorption method, which is mainly used for large volume, high Concentration and solubility of waste gas, but the treatment efficiency of waste gas with poor solubility is low; activated carbon adsorption method is suitable for low concentration and large volume of VOCs waste gas, activated carbon is easy to absorb and saturate, and the cost of replacing the adsorbent is expensive and the activated carbon after adsorption is saturated It needs to be treated as a kind of hazardous waste; the combustion method is mainly aimed at organic waste gas with high concentration and complex components. This method has simple process and high removal efficiency. The combination of adsorption and combustion is not only suitable for treating waste gas with different concentrations and components, but also has high removal efficiency.
且吸附、燃烧结合法处理VOCs废气的传统装置有两种运行方式:(1)直排式,直接将脱附后的有机废气输送到换热器和催化燃烧室进行燃烧降解,该方法的不足在于系统启动初期由于催化燃烧室的温度较低,部分有机废气由于不能充分燃烧而生成有害中间产物,或未经燃烧被直接排放,且尾气中的热能难以充分利用;(2)内循环式,脱附后的有机废气燃烧后循环进入到活性炭吸附装置作为脱附气进行脱附,该方法的不足之处在于系统结构较复杂,循环气体可能会造成活性炭吸附装置内部有机废气浓度过高,局部温度过高,导致爆炸、起火等安全隐患。And the traditional device for treating VOCs waste gas by the combination of adsorption and combustion has two operating modes: (1) direct exhaust type, which directly transports the desorbed organic waste gas to the heat exchanger and catalytic combustion chamber for combustion and degradation. Because the temperature of the catalytic combustion chamber is low at the beginning of the system start-up, some organic waste gas will generate harmful intermediate products due to incomplete combustion, or be directly discharged without combustion, and the heat energy in the exhaust gas is difficult to fully utilize; (2) Internal circulation type, The desorbed organic waste gas is combusted and circulated into the activated carbon adsorption device as desorption gas for desorption. The disadvantage of this method is that the system structure is relatively complicated, and the circulating gas may cause the concentration of organic waste gas inside the activated carbon adsorption device to be too high. If the temperature is too high, it will cause explosion, fire and other safety hazards.
因而,有必要提供一种安全高效且又能够节省大量资源的废气处理系统。Therefore, it is necessary to provide a safe and efficient exhaust gas treatment system that can save a lot of resources.
发明内容Contents of the invention
针对现有技术存在的不足,本发明的目的在于提供一种净化挥发性有机废气的预热式催化燃烧系统,其不仅能够快速有效地去除废气中的VOCs废气,同时其也能够对回收大量的有机溶剂,因而提高环境保护和资源节约方面都具有较高的效益。In view of the deficiencies in the prior art, the purpose of the present invention is to provide a preheating catalytic combustion system for purifying volatile organic waste gas, which can not only quickly and effectively remove VOCs waste gas in the waste gas, but also recover a large amount of VOCs Organic solvents, thus improving environmental protection and resource conservation have higher benefits.
为实现上述目的,本发明提供了如下技术方案:一种净化挥发性有机废气的预热式催化燃烧系统,依次连通有压缩储存单元、吸附单元和催化燃烧单元,所述压缩储存单元包括容器腔、将VOCs废气通入至容器腔中的鼓风机和连通容器腔与吸附单元的调节阀,并且容器腔与鼓风机之间带有干燥剂容器;所述吸附单元包括依次连通的冷凝器和活性碳吸附装置,所述活性炭吸附装置内带有加热器,且活性炭吸附装置分别与催化燃烧单元和鼓风机相连通;所述催化燃烧单元包括催化床和燃烧器,所述燃烧器朝向于催化床,所述催化床与烟囱相连通,且所述烟囱中带有换热器,所述换热器的冷流管与吸附单元和燃烧器相连通。In order to achieve the above object, the present invention provides the following technical solution: a preheating catalytic combustion system for purifying volatile organic waste gas, which is sequentially connected with a compression storage unit, an adsorption unit and a catalytic combustion unit, and the compression storage unit includes a container cavity 1. The blower that passes the VOCs exhaust gas into the container cavity and the regulating valve that communicates the container cavity with the adsorption unit, and there is a desiccant container between the container cavity and the blower; the adsorption unit includes sequentially connected condensers and activated carbon adsorption device, the activated carbon adsorption device is equipped with a heater, and the activated carbon adsorption device is respectively connected with the catalytic combustion unit and the blower; the catalytic combustion unit includes a catalytic bed and a burner, and the burner faces the catalytic bed, and the The catalytic bed is communicated with the chimney, and the chimney is provided with a heat exchanger, and the cold flow pipe of the heat exchanger is communicated with the adsorption unit and the burner.
通过采用上述技术方案,鼓风机将VOCs废气以较高流速吹入到容器腔中,然后操作调节阀,以改变容器腔的进气速度和出气速度之间的关系,从而使得VOCs废气能够在容器腔中进行缓冲,避免了VOCs废气在系统中流速过大,而影响到净化的效率,进而减少了对系统造成侵蚀的可能性。By adopting the above technical solution, the blower blows the VOCs exhaust gas into the container cavity at a higher flow rate, and then operates the regulating valve to change the relationship between the intake velocity and the output velocity of the container cavity, so that the VOCs exhaust gas can flow in the container cavity Buffering in the middle avoids the excessive flow rate of VOCs exhaust gas in the system, which affects the efficiency of purification, thereby reducing the possibility of corrosion to the system.
其次,冷凝器能够对从容器腔出来的VOCs废气进行冷凝,而活性炭吸附装置能够对废气中剩余的VOCs成份进行吸附,之后剩余的废气就会进入到催化燃烧单元中。等到活性炭吸附装置吸附饱和的时候,此时,关闭VOCs废气的进入,并利用加热器对活性炭吸附装置中的活性炭进行加热,使得被吸附的VOCs废气解吸出来,并且回流至鼓风机处。Secondly, the condenser can condense the VOCs exhaust gas coming out of the container cavity, and the activated carbon adsorption device can absorb the remaining VOCs components in the exhaust gas, and then the remaining exhaust gas will enter the catalytic combustion unit. When the activated carbon adsorption device is saturated, at this time, close the entry of VOCs exhaust gas, and use the heater to heat the activated carbon in the activated carbon adsorption device, so that the adsorbed VOCs exhaust gas is desorbed and returned to the blower.
而进入到催化燃烧单元的VOCs废气,其首先会经过换热器被预热,之后其就会流至到燃烧器处被点燃,之后废气就会流至催化床处,在催化剂和余温的作用下,剩余的有机废气就会被催化氧化。经过上述处理之后的最终废气,其还会再经过换热器,利用余热对进入换热器中的VOCs废气进行加热,从而有助于增加VOCs废气的温度,进而不仅提高了最终废气的燃烧效率,同时也减少了热能的浪费。The VOCs exhaust gas entering the catalytic combustion unit will first be preheated by the heat exchanger, then it will flow to the burner to be ignited, and then the exhaust gas will flow to the catalytic bed, where the catalyst and residual temperature will be separated. Under the action, the remaining organic waste gas will be catalyzed and oxidized. After the above-mentioned treatment, the final exhaust gas will pass through the heat exchanger again, and the waste heat will be used to heat the VOCs exhaust gas entering the heat exchanger, which will help to increase the temperature of the VOCs exhaust gas, thereby not only improving the combustion efficiency of the final exhaust gas , but also reduce the waste of heat energy.
优选为,所述容器腔的顶部与底部之间设置有若干液体附着网,同时,容器腔的底部带有卸料阀。Preferably, several liquid attachment nets are arranged between the top and the bottom of the container cavity, and meanwhile, the bottom of the container cavity is equipped with a discharge valve.
通过采用上述技术方案,液体附着网是由钢丝编制而成的网,其能够为VOCs废气提供附着点,从而一方面方便了VOCs废气在液体附着网上液化,从而对液化后的有机溶剂进行了导流作用。另一方面,液体附着网也能够对VOCs废气起到过滤作用,减少过大的固体杂物进入到系统中,而造成系统的损坏。再者,当容器腔中的有机溶剂过多的时候,工作人员只要打开卸料阀,就能够使有机溶剂在容器腔内的压力作用下,输送至指定地点,从而也就提高了输送效率。By adopting the above technical scheme, the liquid attachment net is a net made of steel wire, which can provide attachment points for VOCs waste gas, so that on the one hand, it facilitates the liquefaction of VOCs waste gas on the liquid attachment net, thereby guiding the liquefied organic solvent. flow effect. On the other hand, the liquid attachment net can also filter VOCs exhaust gas, reducing excessive solid debris from entering the system and causing damage to the system. Furthermore, when there is too much organic solvent in the container cavity, the staff only needs to open the discharge valve, and the organic solvent can be transported to the designated place under the pressure in the container cavity, thereby improving the transport efficiency.
优选为,所述容器腔的外周面上分布用于冷却容器腔内部废气的冷却管道。Preferably, cooling pipes for cooling exhaust gas inside the container cavity are distributed on the outer peripheral surface of the container cavity.
通过采用上述技术方案,冷却管道能够从容器腔外对容器腔内的VOCs废气进行冷凝,由于容器腔内的环境是高压低温的情况,所以VOCs废气更容易发生液化。从而有利于提高VOCs废气的净化效率。By adopting the above technical solution, the cooling pipeline can condense the VOCs exhaust gas in the container cavity from outside the container cavity. Since the environment in the container cavity is high pressure and low temperature, the VOCs exhaust gas is more likely to liquefy. Thereby, it is beneficial to improve the purification efficiency of VOCs exhaust gas.
优选为,所述活性炭吸附装置的数量多于一个,且是并联设置的。Preferably, the number of the activated carbon adsorption devices is more than one, and they are arranged in parallel.
通过采用上述技术方案,这样当其中一个活性炭吸附装置吸附饱和的时候,工作人员只要将VOCs废气切换到另外的活性炭吸附装置即可,从而一方面能够保证对VOCs废气的连续化处理,另一方面也不会影响到活性炭吸附装置的解吸操作。进而提高了吸附单元的整体操作效率。By adopting the above technical scheme, when one of the activated carbon adsorption devices is saturated, the staff only need to switch the VOCs exhaust gas to another activated carbon adsorption device, so that on the one hand, it can ensure the continuous treatment of VOCs exhaust gas, on the other hand It will not affect the desorption operation of the activated carbon adsorption device. This in turn increases the overall operating efficiency of the adsorption unit.
优选为,所述加热器为与烟囱相连通的热风管和加热丝,所述热风管朝向于活性炭吸附装置的活性炭,而加热丝位于热风管与活性炭之间。Preferably, the heater is a hot air pipe and a heating wire connected to the chimney, the hot air pipe faces the activated carbon of the activated carbon adsorption device, and the heating wire is located between the hot air pipe and the activated carbon.
通过采用上述技术方案,由于烟囱出来的废气基本上已是无机废气了,但是其还带有大量的余热,因而利用它来对活性炭吸附装置进行解吸操作,能够进一步提高对热能的合理利用率。同时,加热丝能够对热风管出来的热风进行加热,以保证其能够达到所需的温度。By adopting the above technical solution, since the waste gas from the chimney is basically inorganic waste gas, but it also contains a large amount of waste heat, using it to desorb the activated carbon adsorption device can further improve the rational utilization of heat energy. At the same time, the heating wire can heat the hot air from the hot air pipe to ensure that it can reach the required temperature.
优选为,所述催化床上带有催化剂,所述催化剂为蜂窝状,且催化剂的孔朝向于燃烧器。Preferably, there is a catalyst on the catalyst bed, the catalyst is in a honeycomb shape, and the pores of the catalyst face the burner.
通过采用上述技术方案,由于催化剂是成蜂窝状的,这样有利于增大燃烧后的废气与催化剂接触的面积,从而提高了废气的催化氧化效率。By adopting the above technical solution, since the catalyst is in a honeycomb shape, it is beneficial to increase the contact area between the exhaust gas after combustion and the catalyst, thereby improving the catalytic oxidation efficiency of the exhaust gas.
优选为,所述催化床和燃烧器之前设有阻火罩,所述阻火罩的罩口朝向于燃烧器一侧。Preferably, a flame arresting cover is provided before the catalytic bed and the burner, and the opening of the flame arresting cover faces to the side of the burner.
通过采用上述技术方案,阻火罩有利于对火焰起到一定的阻挡作用,这样能够避免火焰直接燃烧到催化床,而造成催化剂的损坏。而阻火罩朝向于燃烧器,这样能够对火焰起到反向引导作用,从而进一步降低了火焰燃烧到催化床的可能性。By adopting the above technical solution, the flame arresting cover is beneficial to block the flame to a certain extent, so as to avoid the damage of the catalyst caused by the flame directly burning to the catalytic bed. The flame arrester faces the burner, which can reverse the flame, thereby further reducing the possibility of the flame burning to the catalytic bed.
优选为,所述催化剂由镍铬合金、黏土和陶瓷微珠组成,且三者的质量比为10:7:3。Preferably, the catalyst is composed of nickel-chromium alloy, clay and ceramic microbeads, and the mass ratio of the three is 10:7:3.
通过采用上述技术方案,镍铬合金是良好的催化氧化的催化剂,而黏土的加入不仅能够提高催化剂的成型率,同时其有利于提高催化剂内部的粘结强度,从而有助于延长催化剂的使用寿命。而且,由于陶瓷微球的表面有很多的孔隙,因而其也有利于提高催化剂与废气的接触面积。By adopting the above technical scheme, nickel-chromium alloy is a good catalyst for catalytic oxidation, and the addition of clay can not only improve the molding rate of the catalyst, but also help to improve the bonding strength inside the catalyst, thereby helping to prolong the service life of the catalyst . Moreover, since the surface of the ceramic microsphere has many pores, it is also beneficial to increase the contact area between the catalyst and the exhaust gas.
优选为,所述催化床和燃烧器之前设有阻火罩,所述阻火罩的罩口朝向于燃烧器一侧。Preferably, a flame arresting cover is provided before the catalytic bed and the burner, and the opening of the flame arresting cover faces to the side of the burner.
通过采用上述技术方案,阻火罩有利于对火焰起到一定的阻挡作用,这样能够避免火焰直接燃烧到催化床,而造成催化剂的损坏。而阻火罩朝向于燃烧器,这样能够对火焰起到反向引导作用,从而进一步降低了火焰燃烧到催化床的可能性。By adopting the above technical solution, the flame arresting cover is beneficial to block the flame to a certain extent, so as to avoid the damage of the catalyst caused by the flame directly burning to the catalytic bed. The flame arrester faces the burner, which can reverse the flame, thereby further reducing the possibility of the flame burning to the catalytic bed.
优选为,所述烟囱与催化床之间带有喷淋塔,所述喷淋塔的喷淋液为双氧水和饱和氢氧化钙的混合液。Preferably, there is a spray tower between the chimney and the catalytic bed, and the spray liquid of the spray tower is a mixed liquid of hydrogen peroxide and saturated calcium hydroxide.
通过采用上述技术方案,由于双氧水在酸性或中性的情况下容易发生自身的分解,生成水和氧气,而在碱性情况下,其能够保存较长的时间。此处将双氧水和饱和氢氧化钙进行混合作为喷淋液,这样有利于延长喷淋液的活性时间。By adopting the above technical scheme, hydrogen peroxide is easy to decompose itself under acidic or neutral conditions to generate water and oxygen, while under alkaline conditions, it can be stored for a long time. Here, the hydrogen peroxide and saturated calcium hydroxide are mixed as the spray liquid, which is beneficial to prolong the activity time of the spray liquid.
另外,由于经过催化燃烧之后,VOCs废气的主要成份已变成二氧化碳、二氧化硫和水蒸汽等无机废气和少量的有机废气了。而喷淋液中的氢氧化钙能够与无机废气进行复分解反应并生成碳酸钙和硫酸钙沉淀。此时,喷淋液的酸碱度是之间趋于中性或弱酸性了,这样双氧水就会发生分解,产生的氧气能够对剩余微量的有机废气进行氧化反应,从而进一步提高了对VOCs废气的处理能力。In addition, after catalytic combustion, the main components of VOCs exhaust gas have become inorganic exhaust gases such as carbon dioxide, sulfur dioxide and water vapor, and a small amount of organic exhaust gases. The calcium hydroxide in the spray liquid can undergo metathesis reaction with the inorganic waste gas and generate calcium carbonate and calcium sulfate precipitates. At this time, the pH of the spray liquid tends to be neutral or weakly acidic, so that the hydrogen peroxide will decompose, and the oxygen produced can oxidize the remaining traces of organic waste gas, thereby further improving the treatment of VOCs waste gas ability.
优选为,所述喷淋塔内部带有防水紫外灯。Preferably, the spray tower is equipped with a waterproof ultraviolet lamp inside.
通过采用上述技术方案,由于双氧水的分解会产生大量的氧气,而紫外光能够促使氧气发生反应生成臭氧,而臭氧对于有机废气的氧化能力要远远大于普通的氧气,从而也就进一步提高了处理VOCs废气的效率。By adopting the above technical scheme, since the decomposition of hydrogen peroxide will produce a large amount of oxygen, and ultraviolet light can promote the reaction of oxygen to generate ozone, and the oxidation ability of ozone to organic waste gas is much greater than that of ordinary oxygen, thus further improving the treatment efficiency. Efficiency of VOCs exhaust gas.
综上所述,本发明具有以下有益效果:In summary, the present invention has the following beneficial effects:
1、利用燃烧后的废气余热对进入催化燃烧单元的VOCs废气进行预热,这样不仅能够提高燃烧效率,同时也减少了余热的浪费;1. Preheat the VOCs exhaust gas entering the catalytic combustion unit by using the waste heat of the exhaust gas after combustion, which can not only improve the combustion efficiency, but also reduce the waste of waste heat;
2、通过控制容器腔的进风速率和出风速率之差,使得容器腔能够对VOCs起到缓冲的作用,有利于提高整体系统的安全性;2. By controlling the difference between the air inlet rate and the air outlet rate of the container cavity, the container cavity can buffer VOCs, which is conducive to improving the safety of the overall system;
3、利用燃烧后的废气预热对活性炭吸附装置进行加热,从而有利于VOCs废气进行解吸,从而不仅能够提高活性炭吸附装置的操作效率,同时也进一步提高了对余热的利用效率。3. The activated carbon adsorption device is heated by preheating the exhaust gas after combustion, which is beneficial to the desorption of VOCs exhaust gas, which not only improves the operating efficiency of the activated carbon adsorption device, but also further improves the utilization efficiency of waste heat.
附图说明Description of drawings
图1为实施例一的净化挥发性有机废气的预热式催化燃烧系统的结构示意图;Fig. 1 is the schematic structural view of the preheating catalytic combustion system for purifying volatile organic waste gas in Embodiment 1;
图2为实施例一的活性炭吸附装置的结构图示意图;Fig. 2 is the schematic diagram of the structure of the activated carbon adsorption device of embodiment one;
图3为实施例一的催化燃烧单元的结构示意图;Fig. 3 is the structural representation of the catalytic combustion unit of embodiment one;
图4为实施例二的容器腔的结构示意图;Fig. 4 is the structural representation of the container cavity of embodiment two;
图5为实施例三的净化挥发性有机废气的预热式催化燃烧系统的结构示意图;5 is a schematic structural view of a preheating catalytic combustion system for purifying volatile organic waste gas in Embodiment 3;
图6为实施例三的活性炭吸附装置的结构图示意图;Fig. 6 is the schematic diagram of the structure diagram of the activated carbon adsorption device of embodiment three;
图7为实施例四的催化燃烧单元的结构示意图;Fig. 7 is the structural representation of the catalytic combustion unit of embodiment four;
图8为实施例五的净化挥发性有机废气的预热式催化燃烧系统的结构示意图;Fig. 8 is a structural schematic diagram of a preheating catalytic combustion system for purifying volatile organic waste gas in Embodiment 5;
图9为实施例五的喷淋塔的结构示意图。Fig. 9 is a schematic structural view of the spray tower of the fifth embodiment.
附图标记:1、压缩储存单元;11、鼓风机;12、容器腔;121、卸料阀;122、冷却管;123、液体附着网;13、调节阀;14、干燥剂容器;2、吸附单元;21、冷凝器;22、活性炭吸附装置;221、加热器;2211、热风管;2212、加热丝;223、活性碳块;224、切换阀;225、启闭阀;3、催化燃烧单元;31、催化床;32、燃烧器;33、换热器;34、阻火罩;4、烟囱;5、喷淋塔;51、防水紫外灯。Reference signs: 1. Compression storage unit; 11. Blower; 12. Container cavity; 121. Unloading valve; 122. Cooling pipe; 123. Liquid attachment net; 13. Regulating valve; 14. Desiccant container; 2. Adsorption Unit; 21, condenser; 22, activated carbon adsorption device; 221, heater; 2211, hot air pipe; 2212, heating wire; 223, activated carbon block; 224, switching valve; 225, opening and closing valve; 3, catalytic combustion Unit; 31. Catalytic bed; 32. Burner; 33. Heat exchanger; 34. Fire hood; 4. Chimney; 5. Spray tower; 51. Waterproof ultraviolet lamp.
具体实施方式Detailed ways
以下结合附图对本发明作进一步详细说明。The present invention will be described in further detail below in conjunction with the accompanying drawings.
实施例一:Embodiment one:
一种净化挥发性有机废气的预热式催化燃烧系统,如附图1所示,依次连通为压缩储存单元1、吸附单元2和催化燃烧单元3。其中,压缩储存单元1主要由鼓风机11和容器腔12组成,其中鼓风机11的一端直接与VOCs废气产生处相连通,另一端与容器腔12相连通,而容器腔12与吸附单元2相连通。同时,容器腔12和吸附单元2之间还带有调节阀13,调节阀13能够对容器腔12的出风速率进行调控。这样鼓风机11能够将VOCs废气以较高流速吹入到容器腔12中,然后操作调节阀13,以调节容器腔12的进气速度和出气速度的关系,这样容器腔12能够对VOCs废气起到缓冲作用,保证了VOCs废气在系统中流动的稳定性。A preheating catalytic combustion system for purifying volatile organic waste gas, as shown in Figure 1, is sequentially connected to a compression storage unit 1, an adsorption unit 2 and a catalytic combustion unit 3. Among them, the compressed storage unit 1 is mainly composed of a blower 11 and a container cavity 12, wherein one end of the blower 11 is directly connected to the place where VOCs exhaust gas is generated, and the other end is connected to the container cavity 12, and the container cavity 12 is connected to the adsorption unit 2. At the same time, there is a regulating valve 13 between the container chamber 12 and the adsorption unit 2 , and the regulating valve 13 can regulate the air outlet rate of the container chamber 12 . Blower 11 can blow VOCs waste gas into container chamber 12 with higher flow rate like this, then operates regulating valve 13, to regulate the relation of the intake velocity of container chamber 12 and the gas outlet velocity, container chamber 12 can play a role to VOCs waste gas like this The buffering effect ensures the stability of VOCs exhaust gas flowing in the system.
结合附图1和附图2所示,吸附单元2主要由冷凝器21和活性炭吸附装置22组成,其中冷凝器21一端与调节阀13相连通,而另一端与活性炭吸附装置22的底部相连通。活性炭吸附装置22的数量可以根据实际需要来确定,此处活性炭吸附装置22的数量为两个,并且,两活性炭吸附装置22是并联设置的。另外,活性炭吸附装置22内带有平行设置的活性碳块223,且性炭吸附装置在活性炭块下方带有加热器221。而两活性炭吸附装置22的顶部均分别与鼓风机11和催化燃烧单元3相连通,这里每个活性炭吸附装置22的顶部和底部均分别带有切换阀224和启闭阀225。这样当其中一个活性炭吸附装置22吸附饱和的时候,启闭阀225就能够关闭该活性炭吸附装置22,使得废气无法进入到活性炭吸附装置22中。同时。另一个活性炭吸附装置22上的启闭阀225就会打开。而在这个过程中,启闭阀225关闭的活性炭吸附装置22中的加热器221就会加热活性炭块,使得VOCs废气发生解吸,并且此时切换阀224就会使该活性炭吸附装置22与鼓风机11连通而与催化燃烧单元3断开,这样解吸后的VOCs废气就会回流继续进行处理。而另一个活性炭吸附装置22在切换阀224的做下与鼓风机11断开,而与催化燃烧单元3连通。从而也就保证了吸附单元2的连续化生产,进而大幅度提高了整体废气净化系统的效率。As shown in accompanying drawings 1 and 2, the adsorption unit 2 is mainly composed of a condenser 21 and an activated carbon adsorption device 22, wherein one end of the condenser 21 communicates with the regulating valve 13, and the other end communicates with the bottom of the activated carbon adsorption device 22 . The number of activated carbon adsorption devices 22 can be determined according to actual needs, here the number of activated carbon adsorption devices 22 is two, and the two activated carbon adsorption devices 22 are arranged in parallel. In addition, the activated carbon adsorption device 22 has an activated carbon block 223 arranged in parallel, and the activated carbon adsorption device has a heater 221 under the activated carbon block. The tops of the two activated carbon adsorption devices 22 are respectively connected with the blower 11 and the catalytic combustion unit 3 , and the top and bottom of each activated carbon adsorption device 22 are provided with switching valves 224 and opening and closing valves 225 respectively. In this way, when one of the activated carbon adsorption devices 22 is saturated with adsorption, the opening and closing valve 225 can close the activated carbon adsorption device 22 so that exhaust gas cannot enter the activated carbon adsorption device 22 . at the same time. The on-off valve 225 on another activated carbon adsorption device 22 will be opened. In this process, the heater 221 in the activated carbon adsorption device 22 closed by the opening and closing valve 225 will heat the activated carbon block, so that the VOCs waste gas will be desorbed, and at this time, the switching valve 224 will make the activated carbon adsorption device 22 and the blower 11 It is connected and disconnected from the catalytic combustion unit 3, so that the desorbed VOCs exhaust gas will flow back and continue to be processed. And another activated carbon adsorption device 22 is disconnected from the air blower 11 under the operation of the switching valve 224, and communicates with the catalytic combustion unit 3. Therefore, the continuous production of the adsorption unit 2 is ensured, and the efficiency of the overall exhaust gas purification system is greatly improved.
另外,结合附图1和附图3所示,催化燃烧单元3主要包括了催化床31和燃烧器32,其中燃烧器32与催化床31连通,并且燃烧器32朝向于催化床31。而催化床31还与一烟囱4相连通。同时,烟囱4与催化床31之间带有一个换热器33,换热器33中的热流管与催化床31和烟囱4相连通,而冷流管与吸附单元2和燃烧器32相连通。这样吸附后的废气能够被催化燃烧后的废气加热,如此循环有利于提高有机废气对余热的利用率。另外,当被燃烧的VOCs废气因浓度过低无法燃烧的时候,可以向燃烧器添加燃料对VOCs废气进行燃烧。In addition, as shown in FIG. 1 and FIG. 3 , the catalytic combustion unit 3 mainly includes a catalytic bed 31 and a burner 32 , wherein the burner 32 communicates with the catalytic bed 31 and the burner 32 faces the catalytic bed 31 . The catalytic bed 31 is also in communication with a chimney 4 . Simultaneously, there is a heat exchanger 33 between the chimney 4 and the catalytic bed 31, the heat flow pipe in the heat exchanger 33 communicates with the catalytic bed 31 and the chimney 4, and the cold flow pipe communicates with the adsorption unit 2 and the burner 32 . In this way, the exhaust gas after adsorption can be heated by the exhaust gas after catalytic combustion, and such circulation is conducive to improving the utilization rate of waste heat by organic waste gas. In addition, when the burned VOCs exhaust gas cannot be burned due to its low concentration, fuel can be added to the burner to burn the VOCs exhaust gas.
实施例二:Embodiment two:
一种净化挥发性有机废气的预热式催化燃烧系统,如附图4所示,基于实施例一的基础上,容器腔12的外周面还带有冷却管122,冷却管122内流动有冷却液。而该冷却液能够对容器腔12内的VOCs废气进行冷却,有助于VOCs废气的液化效率。同时,容器腔12顶部和底部之间连接有若干液体附着网123,液体附着网123数量可以根据实际情况来确定。通过液体附着网123能够为VOCs废气提供附着点,这样一方面有利于提高VOCs废气的液化效率,另一方面也能够提高对液化后的有机溶剂起到导流作用,使其能够尽快流至容器腔12底部。再者,此处的容器腔12底部还带有卸料阀121,这样当容器腔12中的有机溶剂过多的时候,工作人员只要打开卸料阀121,就能够使有机溶剂在容器腔12内的压力作用下,输送至指定地点,从而也就提高了输送效率。A preheating catalytic combustion system for purifying volatile organic waste gas, as shown in Figure 4, on the basis of Embodiment 1, the outer peripheral surface of the container cavity 12 is also provided with a cooling pipe 122, and cooling pipes 122 flow therein. liquid. The cooling liquid can cool the VOCs exhaust gas in the container chamber 12, and contribute to the liquefaction efficiency of the VOCs exhaust gas. At the same time, a number of liquid attachment nets 123 are connected between the top and bottom of the container chamber 12, and the number of liquid attachment nets 123 can be determined according to actual conditions. The liquid attachment network 123 can provide attachment points for the VOCs waste gas, which on the one hand helps to improve the liquefaction efficiency of the VOCs waste gas, and on the other hand can also improve the diversion of the liquefied organic solvent so that it can flow to the container as soon as possible Cavity 12 bottom. Moreover, the bottom of the container chamber 12 here also has a discharge valve 121, so that when the organic solvent in the container chamber 12 is too much, the staff only needs to open the discharge valve 121, and the organic solvent can be discharged in the container chamber 12. Under the action of internal pressure, it is transported to the designated place, thus improving the transport efficiency.
实施例三:Embodiment three:
一种净化挥发性有机废气的预热式催化燃烧系统,结合附图5和附图6所示,基于实施例二的基础上,此处加热器221为与烟囱4连通的热风管2211和加热丝2212,热风管2211朝向于活性炭吸附装置22的活性炭,而加热丝2212位于热风管2211与活性炭之间。这样一方面能够对燃烧后的废气余热进行高效的利用,另一方面也能够通过加热丝2212对来自烟囱4的废气进行加热,使其达到所需的温度,这样便于活性炭进行解吸。A preheating catalytic combustion system for purifying volatile organic waste gas, shown in conjunction with accompanying drawings 5 and 6, based on the second embodiment, where the heater 221 is a hot air pipe 2211 communicating with the chimney 4 and The heating wire 2212 and the hot air pipe 2211 are facing the activated carbon of the activated carbon adsorption device 22, and the heating wire 2212 is located between the hot air pipe 2211 and the activated carbon. In this way, on the one hand, the residual heat of the exhaust gas after combustion can be efficiently utilized, and on the other hand, the exhaust gas from the chimney 4 can be heated through the heating wire 2212 to reach the required temperature, which facilitates the desorption of the activated carbon.
实施例四:Embodiment four:
一种净化挥发性有机废气的预热式催化燃烧系统,如附图7所示,基于实施例三的基础上,催化床31上的催化剂为成蜂窝状,并且其孔朝向于燃烧器32。同时,催化剂311由镍铬合金、黏土和陶瓷微珠组成,且三者的质量比为10:7:3。这样一方面在镍铬合金的作用下能够提高废气的催化氧化效率,另一方面黏土有利于提高催化剂的结构强度,再者陶瓷微球和催化剂本身的孔隙都增大了催化剂与废气接触的面积,这样有利于提高废气的催化氧化的效率。另外,此处的催化床31和燃烧器32之间还带有一个罩口朝向燃烧器32的阻火罩34,这样能够减少火焰直接燃烧到催化剂的概率,从而有利于延长催化剂的使用寿命。A preheating catalytic combustion system for purifying volatile organic waste gas, as shown in FIG. 7 , based on the third embodiment, the catalyst on the catalytic bed 31 is honeycomb-shaped, and its holes face the burner 32 . Meanwhile, the catalyst 311 is composed of nickel-chromium alloy, clay and ceramic microbeads, and the mass ratio of the three is 10:7:3. In this way, on the one hand, the catalytic oxidation efficiency of exhaust gas can be improved under the action of nickel-chromium alloy, on the other hand, clay is beneficial to improve the structural strength of the catalyst, and the pores of the ceramic microspheres and the catalyst itself increase the contact area between the catalyst and the exhaust gas. , which is conducive to improving the efficiency of catalytic oxidation of exhaust gas. In addition, there is a flame arresting cover 34 between the catalytic bed 31 and the burner 32 with the cover opening facing the burner 32, which can reduce the probability of direct combustion of the flame to the catalyst, thereby helping to prolong the service life of the catalyst.
实施例五:Embodiment five:
一种净化挥发性有机废气的预热式催化燃烧系统,结合附图8和附图9所示,基于实施例四的基础上,烟囱4与催化床31之间带有喷淋塔5,具体位置为换热器33和烟囱4之间。并且,此处喷淋塔5的喷淋液为双氧水和饱和氢氧化钙的混合液,体积比为摩尔比为2;1。由于经过催化燃烧后的VOCs废气的主要成份已变成二氧化碳、二氧化硫和水蒸汽等无机废气和少量的有机废气了。而喷淋液中的氢氧化钙能够与无机废气进行复分解反应并生成碳酸钙和硫酸钙沉淀。此时,喷淋液的酸碱度是之间趋于中性或弱酸性了,这样双氧水就会发生分解,产生的氧气能够对剩余微量的有机废气进行氧化反应,从而进一步提高了对VOCs废气的处理能力。A preheating catalytic combustion system for purifying volatile organic waste gas, as shown in Figure 8 and Figure 9, based on Embodiment 4, there is a spray tower 5 between the chimney 4 and the catalytic bed 31, specifically The location is between the heat exchanger 33 and the chimney 4 . In addition, the spray liquid in the spray tower 5 is a mixture of hydrogen peroxide and saturated calcium hydroxide, and the volume ratio is 2;1. Because the main components of VOCs exhaust gas after catalytic combustion have become inorganic exhaust gases such as carbon dioxide, sulfur dioxide and water vapor, and a small amount of organic exhaust gases. The calcium hydroxide in the spray liquid can undergo metathesis reaction with the inorganic waste gas and generate calcium carbonate and calcium sulfate precipitates. At this time, the pH of the spray liquid tends to be neutral or weakly acidic, so that the hydrogen peroxide will decompose, and the oxygen produced can oxidize the remaining traces of organic waste gas, thereby further improving the treatment of VOCs waste gas ability.
另外,在喷淋塔5内部带有防水紫外灯51,防水紫外灯51产生的紫外线能够促使促使双氧水分解产生的氧气发生反应生成臭氧,而臭氧对于有机废气的氧化能力要远远大于普通的氧气,从而也就进一步提高了处理VOCs废气的效率。In addition, there is a waterproof ultraviolet lamp 51 inside the spray tower 5. The ultraviolet rays generated by the waterproof ultraviolet lamp 51 can promote the reaction of oxygen generated by the decomposition of hydrogen peroxide to generate ozone, and the oxidation ability of ozone for organic waste gas is much greater than that of ordinary oxygen. , thus further improving the efficiency of treating VOCs exhaust gas.
再者,鼓风机11和容器腔12之间还连通有一个干燥剂容器14,干燥剂容器14中的干燥剂选取可以根据实际情况来选择,此处采用的是氧化铝和明矾等干燥剂,这样能够对VOCs废气预脱水,从而有利于提高液化下来的有机溶剂的纯度。并且此处干燥剂容器14的数量为两个,且是成并联设置的。同时,烟囱还与两干燥剂容器14分别相连通,这样当一个干燥剂容器14中的干燥剂吸收水分饱和的时候,VOCs废气就可以被切换到另一个干燥剂容器14中,之后烟囱4中燃烧后的热空气就能够对饱和的干燥剂进行干燥,从而也就实现了干燥剂的循环使用。Furthermore, a desiccant container 14 is also communicated between the air blower 11 and the container chamber 12, and the selection of the desiccant in the desiccant container 14 can be selected according to the actual situation. Here, desiccants such as aluminum oxide and alum are used, so that It can pre-dehydrate VOCs waste gas, which is beneficial to improve the purity of the liquefied organic solvent. And here the number of desiccant containers 14 is two, and they are arranged in parallel. Simultaneously, the chimney is also connected with the two desiccant containers 14 respectively, so that when the desiccant in one desiccant container 14 absorbs moisture and is saturated, the VOCs waste gas can be switched to another desiccant container 14, and then in the chimney 4 The hot air after combustion can dry the saturated desiccant, thus realizing the recycling of the desiccant.
本具体实施例仅仅是对本发明的解释,其并不是对本发明的限制,本领域技术人员在阅读完本说明书后可以根据需要对本实施例做出没有创造性贡献的修改,但只要在本发明的权利要求范围内都受到专利法的保护。This specific embodiment is only an explanation of the present invention, and it is not a limitation of the present invention. Those skilled in the art can make modifications to this embodiment without creative contribution as required after reading this specification, but as long as they are within the rights of the present invention All claims are protected by patent law.
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Cited By (8)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN109985476A (en) * | 2019-03-01 | 2019-07-09 | 赵德华 | VOCS device in a kind of efficient process toxic gas |
CN110433873A (en) * | 2019-08-13 | 2019-11-12 | 浙江德创环保科技股份有限公司 | A kind of honeycomb type denitrification catalyst rapid draing and method for calcinating |
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CN116603361A (en) * | 2023-07-21 | 2023-08-18 | 天津市英格环保科技有限公司 | Waste gas treatment device for traditional Chinese medicine processing |
Citations (9)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
EP0393515A1 (en) * | 1989-04-17 | 1990-10-24 | S.S.T. SOLID STATE TECHNOLOGIES S.r.L. | Plant for purifying air polluted with organic industrial products, by catalytic combustion |
KR20080097500A (en) * | 2007-05-02 | 2008-11-06 | 주식회사 엔바이온 | Odor and volatile organic compound treatment system |
CN105289197A (en) * | 2015-11-19 | 2016-02-03 | 苏州韵蓝环保科技有限公司 | Exhaust gas purifier by using double methods |
CN105457329A (en) * | 2014-08-26 | 2016-04-06 | 湖北三宁化工股份有限公司 | Cyclohexane oxidation tail gas recycling device |
CN205435380U (en) * | 2016-03-03 | 2016-08-10 | 杭州辰睿空分设备制造有限公司 | Quick detachable alarm device of cylinder that adsorption tower molecular sieve compressed tightly |
CN106422647A (en) * | 2016-11-15 | 2017-02-22 | 杭州捷瑞空气处理设备有限公司 | Low-liquidus-temperature organic waste gas recycling apparatus |
CN106669292A (en) * | 2015-11-11 | 2017-05-17 | 苏州超等环保科技有限公司 | Water vapor particle separation device |
CN106902838A (en) * | 2017-03-06 | 2017-06-30 | 西南化工研究设计院有限公司 | One kind catalysis burning VOCs monoblock types composite catalyst, preparation method and application |
CN208642286U (en) * | 2018-07-04 | 2019-03-26 | 宁波大学 | A preheating catalytic combustion system for purifying volatile organic waste gas |
-
2018
- 2018-07-04 CN CN201810726442.2A patent/CN108554150B/en active Active
Patent Citations (9)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
EP0393515A1 (en) * | 1989-04-17 | 1990-10-24 | S.S.T. SOLID STATE TECHNOLOGIES S.r.L. | Plant for purifying air polluted with organic industrial products, by catalytic combustion |
KR20080097500A (en) * | 2007-05-02 | 2008-11-06 | 주식회사 엔바이온 | Odor and volatile organic compound treatment system |
CN105457329A (en) * | 2014-08-26 | 2016-04-06 | 湖北三宁化工股份有限公司 | Cyclohexane oxidation tail gas recycling device |
CN106669292A (en) * | 2015-11-11 | 2017-05-17 | 苏州超等环保科技有限公司 | Water vapor particle separation device |
CN105289197A (en) * | 2015-11-19 | 2016-02-03 | 苏州韵蓝环保科技有限公司 | Exhaust gas purifier by using double methods |
CN205435380U (en) * | 2016-03-03 | 2016-08-10 | 杭州辰睿空分设备制造有限公司 | Quick detachable alarm device of cylinder that adsorption tower molecular sieve compressed tightly |
CN106422647A (en) * | 2016-11-15 | 2017-02-22 | 杭州捷瑞空气处理设备有限公司 | Low-liquidus-temperature organic waste gas recycling apparatus |
CN106902838A (en) * | 2017-03-06 | 2017-06-30 | 西南化工研究设计院有限公司 | One kind catalysis burning VOCs monoblock types composite catalyst, preparation method and application |
CN208642286U (en) * | 2018-07-04 | 2019-03-26 | 宁波大学 | A preheating catalytic combustion system for purifying volatile organic waste gas |
Non-Patent Citations (4)
Title |
---|
张亦飞等编著: "《现代黄金冶炼技术》", 30 September 2014, 冶金工业出版社, pages: 719 * |
环境保护部环境工程评估中心编: "《环境影响评价案例分析 2016年版》", 31 March 2016, 中国环境出版社, pages: 116 * |
童志权主编: "《工业废气污染控制与利用》", 31 January 1989, 化学工业出版社, pages: 288 * |
贺良震主编: "《染整助剂应用 第2版》", 31 July 2013, 东华大学出版社, pages: 31 * |
Cited By (12)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN109985476A (en) * | 2019-03-01 | 2019-07-09 | 赵德华 | VOCS device in a kind of efficient process toxic gas |
CN109985476B (en) * | 2019-03-01 | 2021-05-11 | 中颉化工科技(上海)有限公司 | VOCS device in high-efficient processing toxicity nature gas |
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