CN203990301U - Volatile organic compound processing device - Google Patents
Volatile organic compound processing device Download PDFInfo
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- CN203990301U CN203990301U CN201420344061.5U CN201420344061U CN203990301U CN 203990301 U CN203990301 U CN 203990301U CN 201420344061 U CN201420344061 U CN 201420344061U CN 203990301 U CN203990301 U CN 203990301U
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- 239000012855 volatile organic compound Substances 0.000 title claims abstract description 77
- 238000003795 desorption Methods 0.000 claims abstract description 93
- 239000003054 catalyst Substances 0.000 claims abstract description 61
- 238000010521 absorption reaction Methods 0.000 claims abstract description 52
- 230000003647 oxidation Effects 0.000 claims abstract description 45
- 238000007254 oxidation reaction Methods 0.000 claims abstract description 45
- 238000001179 sorption measurement Methods 0.000 claims abstract description 40
- 239000007789 gas Substances 0.000 claims description 111
- 230000001590 oxidative effect Effects 0.000 claims description 27
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims description 24
- 239000002912 waste gas Substances 0.000 claims description 19
- 238000007599 discharging Methods 0.000 claims 2
- 230000008676 import Effects 0.000 claims 1
- 238000010276 construction Methods 0.000 abstract description 7
- 238000012423 maintenance Methods 0.000 abstract description 4
- 238000002336 sorption--desorption measurement Methods 0.000 description 14
- 239000000463 material Substances 0.000 description 9
- 238000000034 method Methods 0.000 description 6
- 238000009833 condensation Methods 0.000 description 5
- 230000005494 condensation Effects 0.000 description 5
- CURLTUGMZLYLDI-UHFFFAOYSA-N Carbon dioxide Chemical compound O=C=O CURLTUGMZLYLDI-UHFFFAOYSA-N 0.000 description 4
- 238000010170 biological method Methods 0.000 description 4
- 230000003197 catalytic effect Effects 0.000 description 4
- 239000002351 wastewater Substances 0.000 description 4
- 239000003463 adsorbent Substances 0.000 description 3
- 244000005700 microbiome Species 0.000 description 3
- 238000011084 recovery Methods 0.000 description 3
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 description 2
- 229910002092 carbon dioxide Inorganic materials 0.000 description 2
- 239000001569 carbon dioxide Substances 0.000 description 2
- 150000001875 compounds Chemical class 0.000 description 2
- 238000010586 diagram Methods 0.000 description 2
- 230000000694 effects Effects 0.000 description 2
- 238000005265 energy consumption Methods 0.000 description 2
- 229920006395 saturated elastomer Polymers 0.000 description 2
- 229910021536 Zeolite Inorganic materials 0.000 description 1
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 description 1
- 238000006243 chemical reaction Methods 0.000 description 1
- 239000000470 constituent Substances 0.000 description 1
- 230000007812 deficiency Effects 0.000 description 1
- 230000029087 digestion Effects 0.000 description 1
- HNPSIPDUKPIQMN-UHFFFAOYSA-N dioxosilane;oxo(oxoalumanyloxy)alumane Chemical compound O=[Si]=O.O=[Al]O[Al]=O HNPSIPDUKPIQMN-UHFFFAOYSA-N 0.000 description 1
- 239000005457 ice water Substances 0.000 description 1
- 239000007788 liquid Substances 0.000 description 1
- 239000007791 liquid phase Substances 0.000 description 1
- VUZPPFZMUPKLLV-UHFFFAOYSA-N methane;hydrate Chemical compound C.O VUZPPFZMUPKLLV-UHFFFAOYSA-N 0.000 description 1
- 230000000813 microbial effect Effects 0.000 description 1
- 239000007800 oxidant agent Substances 0.000 description 1
- 229910052760 oxygen Inorganic materials 0.000 description 1
- 239000001301 oxygen Substances 0.000 description 1
- 239000012071 phase Substances 0.000 description 1
- 238000006479 redox reaction Methods 0.000 description 1
- 238000005201 scrubbing Methods 0.000 description 1
- 238000006467 substitution reaction Methods 0.000 description 1
- 239000013589 supplement Substances 0.000 description 1
- 239000002918 waste heat Substances 0.000 description 1
- 238000004065 wastewater treatment Methods 0.000 description 1
- 239000010457 zeolite Substances 0.000 description 1
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- Exhaust Gas Treatment By Means Of Catalyst (AREA)
- Treating Waste Gases (AREA)
Abstract
一种挥发性有机化合物(VOC)处理装置,包括至少二吸/脱附塔、一废气供给管路、一吸附后气体排放管路及一催化剂氧化处理单元,该废气供给管路交替地连通于该些吸/脱附塔而令该吸/脱附塔进行吸附作业,催化剂氧化处理单元同样交替地连通于该些吸/脱附塔以进行脱附作业,该废气供给管路及催化剂氧化处理单元不同时连通于相同的吸/脱附塔,该催化剂氧化处理单元包括一热交换器、一催化剂反应器、一进气单元、一排气单元。本实用新型由吸/脱附塔与催化剂氧化处理单元的互相搭配,可有效去除废气中的VOC,并具有建置成本较低,容易操作、维护等优点。
A volatile organic compound (VOC) treatment device includes at least two absorption/desorption towers, an exhaust gas supply pipeline, a post-adsorption gas exhaust pipeline, and a catalyst oxidation treatment unit. The exhaust gas supply pipeline is alternately connected to the absorption/desorption towers to allow the absorption/desorption towers to perform adsorption operations. The catalyst oxidation treatment unit is also alternately connected to the absorption/desorption towers to perform desorption operations. The exhaust gas supply pipeline and the catalyst oxidation treatment unit are not simultaneously connected to the same absorption/desorption tower. The catalyst oxidation treatment unit includes a heat exchanger, a catalyst reactor, an air intake unit, and an exhaust unit. The utility model can effectively remove VOCs in exhaust gas by matching the absorption/desorption towers and the catalyst oxidation treatment unit, and has the advantages of low construction cost, easy operation and maintenance, etc.
Description
技术领域technical field
本实用新型是关于一种废气处理装置,特别是关于一种挥发性有机化合物处理装置。The utility model relates to a waste gas treatment device, in particular to a volatile organic compound treatment device.
背景技术Background technique
工厂排放的尾气或室内空间经常含有挥发性有机化合物(下称VOC),这些VOC容易对环境及人体造成危害,因此必须实施相应的处理以降低其含量。The tail gas or indoor space emitted by factories often contains volatile organic compounds (hereinafter referred to as VOC), which are likely to cause harm to the environment and human body, so corresponding treatment must be implemented to reduce its content.
洗涤塔是常见的VOC处理装置,由将VOC溶于液相而自气相移除,所使用的洗涤液通常是水,也因此,适用于洗涤塔处理的VOC在水中必须要有较高的溶解度,因此非水溶性的VOC并不适合以洗涤塔进行处理。除此之外,利用洗涤塔处理VOC必然伴随着含VOC废水的产生,而废水也需要经过额外的处理程序并产生废水处理成本,倘废水未经妥善处理即对外排放,废水中的VOC仍会自然逸散而产生恶臭。The scrubber is a common VOC treatment device. It is removed from the gas phase by dissolving VOC in the liquid phase. The scrubbing liquid used is usually water. Therefore, the VOC suitable for scrubber treatment must have a high solubility in water. , so non-water-soluble VOCs are not suitable for treatment with scrubbers. In addition, the use of scrubbers to treat VOC is bound to be accompanied by the generation of VOC-containing wastewater, and the wastewater also needs to undergo additional treatment procedures and generate wastewater treatment costs. If the wastewater is discharged outside without proper treatment, the VOC in the wastewater will still increase. Escaping naturally produces a foul odor.
VOC也可利用生物法加以处理,即利用微生物的消化作用对VOC进行分解,惟生物法占地较大,且微生物培养需要较多时间,因此建置时间较长。为了使微生物能有效率地分解VOC,还必须控制其生长环境的温、湿度,其维持难度较高。此外,由于以生物法处理VOC需花费较长的处理时间,让微生物有足够的时间消化VOC,因此生物法普遍不适用于大量的废气处理。VOC can also be treated by biological methods, that is, the digestion of microorganisms is used to decompose VOCs. However, biological methods occupy a large area and require more time for microbial cultivation, so the construction time is longer. In order for microorganisms to efficiently decompose VOC, the temperature and humidity of their growth environment must be controlled, which is difficult to maintain. In addition, because it takes a long time to treat VOC with biological methods, allowing microorganisms to have enough time to digest VOCs, biological methods are generally not suitable for large-scale waste gas treatment.
以往也有人利用浓缩转轮处理VOC,但由于浓缩转轮的建置成本较高,一般较不受到厂商的青睐,且若工厂尾气中VOC浓度大幅浮动时,固定转速的浓缩转轮将不易有效处理VOC,而若欲调整浓缩转轮的转速,其操控难度又会增加,作业上也会产生其他变量。例如,当工厂尾气中的VOC浓度突然增加时,虽可由提高浓缩转轮的转速以加速吸附VOC,但转速提高的同时也连带缩短了浓缩转轮脱附的时间,导致吸附后的VOC无法被实时脱附,从而降低浓缩转轮后续的吸附性能。In the past, some people used concentrating rotors to treat VOC, but due to the high construction cost of concentrating rotors, they are generally not favored by manufacturers, and if the VOC concentration in the factory exhaust fluctuates greatly, the concentrating rotor with a fixed speed will not be effective To deal with VOC, if you want to adjust the speed of the enrichment wheel, the difficulty of control will increase, and other variables will also occur in the operation. For example, when the concentration of VOC in the factory tail gas suddenly increases, although the speed of the enrichment wheel can be increased to accelerate the adsorption of VOC, but the increase in speed also shortens the desorption time of the concentration wheel, resulting in the VOC after adsorption cannot be absorbed. Real-time desorption, thereby reducing the subsequent adsorption performance of the concentration wheel.
以往还有利用吸/脱附塔搭配蒸气冷凝回收的VOC处理方式,亦即先利用吸/脱附塔进行吸附,饱和后,利用水蒸气进行吸/脱附塔的脱附作业,使VOC被水蒸气夹带脱离吸/脱附塔,随后进行冷凝,让VOC与冷凝水分离,以将VOC加以回收利用。这样的蒸气冷凝回收方式适用于高浓度、单一成分的VOC处理作业,但却有若干缺点在于:In the past, there was a VOC treatment method that used an absorption/desorption tower with steam condensation recovery, that is, the absorption/desorption tower was first used for adsorption, and after saturation, the adsorption/desorption tower was used for desorption with water vapor, so that VOC was The water vapor is carried away from the absorption/desorption tower, and then condensed to separate the VOC from the condensed water, so that the VOC can be recycled. This vapor condensation recovery method is suitable for high-concentration, single-component VOC treatment operations, but it has several disadvantages:
(1)脱附时需使用大量水蒸气及冷凝所需的冰水,因此非常耗能;(1) A large amount of water vapor and ice water required for condensation are used during desorption, so it consumes a lot of energy;
(2)不适用于含多种VOC的废气处理,因为冷凝后还需进行多种VOC之间的分离作业,难度较高;(2) It is not suitable for waste gas treatment containing various VOCs, because after condensation, it is necessary to separate various VOCs, which is difficult;
(3)不适用于低浓度VOC的处理,因为回收所得利益与所耗费能源成本显然不成比例;(3) It is not suitable for the treatment of low-concentration VOC, because the benefits of recovery are obviously not proportional to the cost of energy consumed;
(4)冷凝效率不高,冷凝后的气体中还会含有VOC,且冷凝水中也含有VOC。(4) The condensation efficiency is not high, and the condensed gas also contains VOC, and the condensed water also contains VOC.
有鉴于目前已知的VOC处理装置在实用上仍有诸多不足之处,如何提供一种建置、维护成本较低且能有效处理VOC的处理装置,实值得本领域人士思量的。In view of the fact that currently known VOC processing devices still have many shortcomings in practicality, how to provide a processing device with low construction and maintenance costs and capable of effectively processing VOC is really worthy of consideration by those skilled in the art.
实用新型内容Utility model content
本实用新型的目的是提供一种建置、维护成本较低且能有效处理挥发性有机化合物处理装置The purpose of this utility model is to provide a low construction and maintenance cost and can effectively deal with volatile organic compound treatment device
为实现上述目的,本实用新型提供的挥发性有机化合物处理装置,其包括至少二吸/脱附塔、一废气供给管路、一吸附后气体排放管路及一催化剂氧化处理单元,各该吸/脱附塔具有一进气端及一排气端,该废气供给管路是交替地连通于该些吸/脱附塔的进气端,令该吸/脱附塔进行吸附作业,该吸附后气体排放管路连通于与该废气供给管路连通的吸/脱附塔的排气端,该催化剂氧化处理单元是交替地连通于该些吸/脱附塔以进行脱附作业,该废气供给管路及催化剂氧化处理单元两者并不同时连通于相同的吸/脱附塔,该催化剂氧化处理单元包括一热交换器、一催化剂反应器、一进气单元、一排气单元、一第一管路、一第二管路、一第三管路及一第四管路,该热交换器具有一冷气通道及一热气通道,该冷气通道的一进气口是由该第一管路而与连通于催化剂氧化处理单元的吸/脱附塔的排气端连通,该冷气通道的一排气口由该第二管路而与该催化剂反应器的一进气口连通,该催化剂反应器的一排气口由该第三管路而与该热气通道的一进气口连通,该热气通道的一排气口由该第四管路而与连通于催化剂氧化处理单元的吸/脱附塔的进气端连通,该进气单元连通于第一或第二管路而供导入催化剂反应器所需的氧化气体,该排气单元连通于该第四管路而供排出管路内的部分气体。In order to achieve the above object, the volatile organic compound processing device provided by the utility model includes at least two absorption/desorption towers, a waste gas supply pipeline, a gas discharge pipeline after adsorption and a catalyst oxidation treatment unit, each of which absorbs The/desorption tower has an inlet port and an exhaust port, and the exhaust gas supply pipeline is alternately connected to the inlet ports of the adsorption/desorption towers, so that the adsorption/desorption towers perform adsorption operations, and the adsorption The rear gas discharge pipeline is connected to the exhaust end of the absorption/desorption tower connected with the exhaust gas supply pipeline. The catalytic oxidation treatment unit is alternately connected to the absorption/desorption towers for desorption operation. The exhaust gas The supply pipeline and the catalyst oxidation treatment unit are not connected to the same absorption/desorption tower at the same time, and the catalyst oxidation treatment unit includes a heat exchanger, a catalyst reactor, an air intake unit, an exhaust unit, an A first pipeline, a second pipeline, a third pipeline and a fourth pipeline, the heat exchanger has a cold air passage and a hot air passage, an air inlet of the cold air passage is provided by the first pipeline It communicates with the exhaust end of the absorption/desorption tower connected to the catalyst oxidation treatment unit, and an exhaust port of the cold air channel is communicated with an air inlet of the catalyst reactor by the second pipeline, and the catalyst reacts An exhaust port of the device is communicated with an air inlet of the hot gas channel through the third pipeline, and an exhaust port of the hot gas channel is communicated with the suction/extractor of the catalytic oxidation treatment unit through the fourth pipeline. The inlet end of the attached tower is connected, the inlet unit is connected to the first or second pipeline for the oxidation gas required for introduction into the catalytic reactor, and the exhaust unit is connected to the fourth pipeline for the discharge pipeline part of the gas.
由前述设计,含VOC废气可被吸/脱附塔吸附脱除,当吸附饱和后,可改由催化剂氧化处理单元对该吸/脱附塔进行脱附作业。本实用新型中,催化剂氧化处理单元利用催化剂反应器将VOC氧化为水、二氧化碳等无害的化合物,由于氧化属于放热反应,因此经催化剂反应器处理后的气体还可通过热交换器而对第一管路所输送的脱附气体进行预热,从而减少或免除需额外供给脱附气体的热能,降低能源消耗。整体而言,本实用新型的VOC处理装置具有低建置成本、低耗能、易维护及高处理效率等优点,并可用于处理各种浓度的废气,也能处理同时含有多种VOC的废气,因此本实用新型确实能弥补公知VOC处理装置的不足。According to the aforementioned design, the VOC-containing waste gas can be adsorbed and removed by the absorption/desorption tower. When the adsorption is saturated, the catalyst oxidation treatment unit can be used to perform desorption on the absorption/desorption tower. In the utility model, the catalyst oxidation treatment unit uses the catalyst reactor to oxidize VOC into harmless compounds such as water and carbon dioxide. Since the oxidation is an exothermic reaction, the gas treated by the catalyst reactor can also be treated by the heat exchanger. The desorption gas transported by the first pipeline is preheated, thereby reducing or eliminating the need to additionally supply heat energy of the desorption gas, and reducing energy consumption. Overall, the VOC treatment device of the present invention has the advantages of low construction cost, low energy consumption, easy maintenance and high treatment efficiency, and can be used to treat waste gas of various concentrations, and can also treat waste gas containing multiple VOCs at the same time , so the utility model can really make up for the deficiencies of known VOC treatment devices.
附图说明Description of drawings
图1是本实用新型第一实施例的处理设备组成示意图。Fig. 1 is a schematic diagram of the composition of the processing equipment of the first embodiment of the present invention.
图2是本实用新型第二实施例的处理设备组成示意图。Fig. 2 is a schematic diagram of the composition of the processing equipment of the second embodiment of the present invention.
附图中主要组件符号说明:Explanation of main component symbols in the attached drawings:
吸/脱附塔10a、10b;进气端11a、11b;排气端12a、12b;废气供给管路20;控制阀21、22;吸附后气体排放管路30;吸附风车35;催化剂氧化处理单元40;第一管路41;控制阀411、412;第二管路42;第三管路43;第四管路44;控制阀441、442;热交换器50;冷气通道51;进气口511;排气口512;热气通道52;进气口521;排气口522;催化剂反应器60;进气口61;排气口62;进气单元70;排气单元80;脱附风车90;加热器100;氧化气体传感器110;控制器120;洒水器130;温度传感器140、140a、140b。Absorption/desorption towers 10a, 10b; inlet ports 11a, 11b; exhaust ports 12a, 12b; exhaust gas supply pipeline 20; control valves 21, 22; post-adsorption gas discharge pipeline 30; adsorption windmill 35; catalyst oxidation treatment Unit 40; first pipeline 41; control valves 411, 412; second pipeline 42; third pipeline 43; fourth pipeline 44; control valves 441, 442; heat exchanger 50; cold air channel 51; air intake Port 511; exhaust port 512; hot gas channel 52; air inlet 521; exhaust port 522; catalyst reactor 60; air inlet 61; exhaust port 62; air inlet unit 70; exhaust unit 80; desorption windmill 90; heater 100; oxidizing gas sensor 110; controller 120; sprinkler 130; temperature sensors 140, 140a, 140b.
具体实施方式Detailed ways
请参考图1,在本实用新型的第一实施例中,一种VOC处理装置包括二吸/脱附塔10a、10b、一废气供给管路20、一吸附后气体排放管路30及一催化剂氧化处理单元40。Please refer to Fig. 1, in the first embodiment of the present utility model, a kind of VOC treatment device comprises two absorption/desorption towers 10a, 10b, a waste gas supply pipeline 20, a gas discharge pipeline 30 and a catalyst after an adsorption Oxidation treatment unit 40.
各该吸/脱附塔10a、10b具有一进气端11a、11b及一排气端12a、12b,吸附塔10a、10b内部填充有可吸附VOC的吸附材料,吸附材料的选择是依所需处理的VOC而定,常见的吸附材料包括但不限于活性碳及沸石。Each of the absorption/desorption towers 10a, 10b has an inlet port 11a, 11b and an exhaust port 12a, 12b. The interior of the adsorption towers 10a, 10b is filled with adsorbent materials that can adsorb VOC. The selection of the adsorbent materials depends on the needs. Depending on the VOC to be treated, common adsorbent materials include but are not limited to activated carbon and zeolite.
该废气供给管路20是交替地连通于该些吸/脱附塔10a、10b的进气端11a、11b,废气供给管路20是供导引含有VOC的废气,令该吸/脱附塔10a、10b进行吸附作业,所述「吸附作业」是指VOC被吸附材料吸附的过程,所述「交替地连通于该些吸/脱附塔的进气端」是指废气供给管路在连通于其中一部分吸/脱附塔的进气端一段时间之后,会经过切换而改连通于另一部份吸/脱附塔的进气端一段时间。例如,废气供给管路20首先连通于吸/脱附塔10a的进气端11a,待吸/脱附塔10a即将或已达吸附饱和时,废气供给管路20经过切换而改为连通于吸/脱附塔10b的进气端11b,当吸/脱附塔10b即将或已达吸附饱和时,废气供给管路20又经过切换而连通于吸附塔10a。废气供给管路20可具有若干控制阀21、22而切换所连通的吸/脱附塔10a、10b。The waste gas supply pipeline 20 is alternately communicated with the intake ends 11a, 11b of the absorption/desorption towers 10a, 10b, and the waste gas supply pipeline 20 is used to guide the waste gas containing VOC, so that the absorption/desorption tower 10a, 10b carry out the adsorption operation, the "adsorption operation" refers to the process of VOC being adsorbed by the adsorption material, and the "alternately communicated with the intake ends of these absorption/desorption towers" refers to the waste gas supply pipeline connected to After a period of time at the inlet of one part of the absorption/desorption tower, it will be switched to connect to the inlet of another part of the absorption/desorption tower for a period of time. For example, the exhaust gas supply pipeline 20 is first communicated with the intake port 11a of the absorption/desorption tower 10a, and when the absorption/desorption tower 10a is about to or has reached adsorption saturation, the exhaust gas supply pipeline 20 is changed to communicate with the suction terminal 10a through switching. At the inlet port 11b of the adsorption/desorption tower 10b, when the adsorption/desorption tower 10b is about to or has reached adsorption saturation, the exhaust gas supply pipeline 20 is switched and communicated with the adsorption tower 10a. The exhaust gas supply pipeline 20 may have several control valves 21, 22 to switch the connected absorption/desorption towers 10a, 10b.
该吸附后气体排放管路30是连通于与该废气供给管路20连通的吸/脱附塔10a、10b的排气端12a、12b,换句话说,废气供给管路20与吸附后气体排放管路30是连通于相同的吸/脱附塔10a、10b,前者连通于进气端11a、11b,而后者连通于排气端12a、12b,经吸附后气体排放管路30排出的废气已几乎不含VOC而可直接对外排出。为了将废气自废气供给管路20经由吸/脱附塔10a、10b导引至吸附后气体排放管路30,更可将一吸附风车35设于该吸附后气体排放管路30。This adsorbed gas discharge pipeline 30 is communicated with the exhaust ends 12a, 12b of the absorption/desorption towers 10a, 10b communicating with the exhaust gas supply pipeline 20, in other words, the exhaust gas supply pipeline 20 is connected with the exhaust gas after adsorption. The pipeline 30 is connected to the same absorption/desorption towers 10a, 10b, the former is connected to the inlet ports 11a, 11b, and the latter is connected to the exhaust ports 12a, 12b. After adsorption, the waste gas discharged from the gas discharge pipeline 30 has been It contains almost no VOC and can be discharged directly to the outside. In order to guide the exhaust gas from the exhaust gas supply pipeline 20 to the adsorbed gas discharge pipeline 30 via the adsorption/desorption towers 10a, 10b, an adsorption windmill 35 can be arranged on the adsorbed gas discharge pipeline 30 .
该催化剂氧化处理单元40是交替地连通于该些吸/脱附塔10a、10b以进行脱附作业,且废气供给管路20与催化剂氧化处理单元40不会同时连通于相同的吸/脱附塔10a、10b,亦即单一吸/脱附塔10a、10b不会同时进行吸附作业及脱附作业,所述「脱附作业」是指将VOC自吸附材料中脱附移除的过程。The catalyst oxidation treatment unit 40 is alternately connected to the absorption/desorption towers 10a, 10b for desorption operation, and the exhaust gas supply pipeline 20 and the catalyst oxidation treatment unit 40 are not connected to the same absorption/desorption tower at the same time. The towers 10a, 10b, that is, the single adsorption/desorption towers 10a, 10b do not perform adsorption and desorption operations at the same time. The "desorption operation" refers to the process of desorbing and removing VOC from the adsorption material.
该催化剂氧化处理单元40包括一热交换器50、一催化剂反应器60、一进气单元70、一排气单元80、一第一管路41、一第二管路42、一第三管路43及一第四管路44,该热交换器50具有一冷气通道51及一热气通道52,两者互不连通,冷气通道51内的气体可与热气通道52内的气体进行热交换,冷气通道51及热气通道52的路径并不以图式所示者为限。The catalyst oxidation treatment unit 40 includes a heat exchanger 50, a catalyst reactor 60, an air intake unit 70, an exhaust unit 80, a first pipeline 41, a second pipeline 42, and a third pipeline 43 and a fourth pipeline 44, the heat exchanger 50 has a cold air passage 51 and a hot air passage 52, the two are not connected to each other, the gas in the cold air passage 51 can exchange heat with the gas in the hot air passage 52, and the cold air The paths of the channel 51 and the hot gas channel 52 are not limited to those shown in the figure.
该冷气通道51的一进气口511是由该第一管路41而与连通于催化剂氧化处理单元40的吸/脱附塔10a、10b的排气端12a、12b连通,第一管路41可具有若干控制阀411、412而切换所连通的吸/脱附塔10a、10b,该冷气通道51的一排气口512是由该第二管路42而与该催化剂反应器60的一进气口61连通,催化剂反应器60内部具有可促进VOC氧化的催化剂材料,所选用的催化剂材料依VOC种类而定,催化剂反应器60的一排气口62是由该第三管路43而与热气通道52的一进气口521连通,该热气通道52的一排气口522是由该第四管路44而与连通于催化剂氧化处理单元40的吸/脱附塔10a、10b的进气端11a、11b连通,第四管路44可具有若干控制阀441、442而切换所连通的吸/脱附塔10a、10b。为了让气体能在管路内流动,催化剂氧化处理单元40还可包括一脱附风车90设于第一至第四管路41-44其中之一,在本实施例中则是设于第一管路41。吸附、脱附风车35、90都是用以提供气体流动所需的气压差。An air inlet 511 of the cold air channel 51 is communicated with the exhaust ends 12a, 12b of the adsorption/desorption towers 10a, 10b connected to the catalyst oxidation treatment unit 40 by the first pipeline 41, and the first pipeline 41 A plurality of control valves 411, 412 may be provided to switch the connected absorption/desorption towers 10a, 10b. An exhaust port 512 of the cold air channel 51 is connected to an inlet of the catalyst reactor 60 by the second pipeline 42. Gas port 61 communicates, and catalyst reactor 60 inside has the catalyst material that can promote VOC oxidation, and the catalyst material selected for use depends on VOC kind and decides, and an exhaust port 62 of catalyst reactor 60 is connected with this third pipeline 43 An air inlet 521 of the hot gas channel 52 communicates with an exhaust port 522 of the hot gas channel 52, which is connected to the intake air of the absorption/desorption towers 10a, 10b of the catalyst oxidation treatment unit 40 through the fourth pipeline 44 The ends 11a, 11b are connected, and the fourth pipeline 44 may have several control valves 441, 442 to switch the connected absorption/desorption towers 10a, 10b. In order to allow the gas to flow in the pipeline, the catalyst oxidation treatment unit 40 can also include a desorption windmill 90 arranged in one of the first to fourth pipelines 41-44, in this embodiment it is arranged in the first Line 41. Both the adsorption and desorption windmills 35 and 90 are used to provide the required pressure difference for gas flow.
该进气单元70是连通于第一管路41而供导入催化剂反应器60所需的氧化气体,所述「氧化气体」是指可与VOC进行氧化还原反应的气态氧化剂,例如氧气,进气单元70所导入的氧化气体不一定是纯的氧化气体,也可以是含有氧化气体的混合气体,例如空气。该排气单元80是连通于该第四管路44而供排出管路内的少部分气体,剩余气体则经由第四管路44不断循环至吸/脱附塔10a、10b进行脱附。The air intake unit 70 is connected to the first pipeline 41 for introducing the oxidizing gas required for the catalytic reactor 60. The "oxidizing gas" refers to a gaseous oxidant that can perform a redox reaction with VOC, such as oxygen, and the intake air The oxidizing gas introduced by the unit 70 is not necessarily a pure oxidizing gas, but may also be a mixed gas containing an oxidizing gas, such as air. The exhaust unit 80 is connected to the fourth pipeline 44 to discharge a small amount of gas in the pipeline, and the remaining gas is continuously circulated to the adsorption/desorption towers 10a and 10b through the fourth pipeline 44 for desorption.
工作时,废气供给管路20将含VOC废气导入其中一吸/脱附塔(以吸/脱附塔10a为例)进行吸附作业,吸附处理后的废气由吸附后气体排放管路30直接对外排出或进行后续处理,当吸/脱附塔10a即将或已达吸附饱和时,废气供给管路20改将含VOC废气导入另一吸/脱附塔10b继续进行脱附作业,而吸/脱附塔10a则改与催化剂氧化处理单元40连通并进行脱附作业,此时催化剂氧化处理单元40管路内的脱附气体将吸/脱附塔10a所吸附的VOC脱出,含VOC的脱附气体经由第一管路41导入热交换器50的冷气通道51,同时进气单元70补充氧化气体至含VOC脱附气体中,含VOC脱附气体在热交换器50预热后经第二管路42导入催化剂反应器60,VOC经催化剂氧化处理后转化为二氧化碳及水等无害的化合物,经催化剂处理后的气体再经由第三管路43导入热交换器50的热气通道52,此时高热的气体将热能交换给冷气通道51内的含VOC脱附气体,之后少部分气体经由排气单元80排出,其余气体作为脱附气体继续经由第四管路44循环至吸/脱附塔10a进行脱附作业。当吸/脱附塔10b吸附饱和后,再次进行切换使吸/脱附塔10a复又进行吸附作业,而吸/脱附塔10b则改进行脱附作业。由此,吸/脱附塔10a、10b不断交替切换进行吸附作业与脱附作业,处理后的气体大部分由吸附后气体排放管路30排出,少部分由排气单元80排出,VOC在本处理装置中可被有效地去除。During operation, the exhaust gas supply pipeline 20 will introduce the VOC-containing exhaust gas into one of the absorption/desorption towers (take the absorption/desorption tower 10a as an example) for adsorption operation, and the exhaust gas after adsorption treatment will be directly discharged from the adsorbed gas discharge pipeline 30. discharge or carry out follow-up treatment, when the absorption/desorption tower 10a is about to or has reached adsorption saturation, the waste gas supply pipeline 20 changes the VOC-containing waste gas into another absorption/desorption tower 10b to continue the desorption operation, and the absorption/desorption The adsorption tower 10a is changed to communicate with the catalyst oxidation treatment unit 40 and carry out the desorption operation. At this time, the desorption gas in the pipeline of the catalyst oxidation treatment unit 40 will remove the VOC adsorbed by the absorption/desorption tower 10a, and the desorption containing VOC The gas is introduced into the cold air channel 51 of the heat exchanger 50 through the first pipeline 41, and at the same time, the air intake unit 70 supplements the oxidizing gas into the VOC-containing desorbed gas, and the VOC-containing desorbed gas passes through the second pipe after being preheated by the heat exchanger 50. The road 42 is introduced into the catalyst reactor 60, and VOC is converted into harmless compounds such as carbon dioxide and water after being oxidized by the catalyst, and the gas treated by the catalyst is then introduced into the hot gas channel 52 of the heat exchanger 50 through the third pipeline 43. The high-heat gas exchanges heat energy to the VOC-containing desorbed gas in the cold air channel 51, and then a small part of the gas is discharged through the exhaust unit 80, and the rest of the gas continues to circulate as desorbed gas through the fourth pipeline 44 to the adsorption/desorption tower 10a Perform detachment work. When the absorption/desorption tower 10b is saturated, switch again to make the absorption/desorption tower 10a resume the adsorption operation, while the absorption/desorption tower 10b is changed to perform the desorption operation. As a result, the adsorption/desorption towers 10a, 10b alternately switch between the adsorption operation and the desorption operation. Most of the gas after treatment is discharged from the gas discharge pipeline 30 after adsorption, and a small part is discharged from the exhaust unit 80. can be efficiently removed in processing plants.
基于前述设计,本实用新型的吸/脱附塔及催化剂氧化处理单元的建置成本较低,容易操作、维护,且本实用新型善用VOC氧化后的余热在热交换器内对含有VOC的脱附气体进行预热,可以节省加热脱附气体所需的能源,最终也可有效地去除废气中的VOC。Based on the aforementioned design, the construction cost of the absorption/desorption tower and catalyst oxidation treatment unit of the present invention is relatively low, and it is easy to operate and maintain, and the present invention makes good use of the waste heat after VOC oxidation to treat VOC-containing VOC in the heat exchanger. Preheating the desorbed gas can save the energy needed to heat the desorbed gas, and finally effectively remove VOCs in the exhaust gas.
在本较佳实施例中,催化剂氧化处理单元40还包括一加热器100设于该第二管路42,加热器100用来对已预先升温的脱附气体进一步加热至催化剂反应器60所需的工作温度,惟若脱附气体在热交换器50中已可升温至催化剂反应器60所需的工作温度,则该加热器100也可省略或不作用。In this preferred embodiment, the catalyst oxidation treatment unit 40 also includes a heater 100 disposed in the second pipeline 42, and the heater 100 is used to further heat the pre-heated desorption gas to the catalyst reactor 60. However, if the temperature of the desorbed gas in the heat exchanger 50 can be raised to the required working temperature of the catalyst reactor 60, then the heater 100 can also be omitted or have no effect.
在本较佳实施例中,为了精准控制氧化气体的补充量,该催化剂氧化处理单元60还可包括一氧化气体传感器110及一控制器120,该氧化气体传感器110设于第四管路44而供感测管路内的氧化气体含量,该控制器120电性连接于进气单元70、排气单元80及氧化气体传感器110,且控制器120可根据氧化气体传感器110所感测的讯号而精准控制进气单元70的进气量,同时根据进气单元70的进气量而相应地控制排气单元80的排气量,亦即令补充至催化剂氧化处理单元40的流量与自催化剂氧化处理单元40排出的流量约略相等,使管路内部流量保持稳定,以利控制脱附作业的进行。In this preferred embodiment, in order to accurately control the supplementary amount of the oxidizing gas, the catalyst oxidation treatment unit 60 may further include an oxidizing gas sensor 110 and a controller 120, the oxidizing gas sensor 110 is arranged in the fourth pipeline 44 and For sensing the oxidizing gas content in the pipeline, the controller 120 is electrically connected to the intake unit 70 , the exhaust unit 80 and the oxidizing gas sensor 110 , and the controller 120 can be accurately and precisely based on the signal sensed by the oxidizing gas sensor 110 Control the intake air volume of the air intake unit 70, and correspondingly control the exhaust air volume of the exhaust unit 80 according to the intake air volume of the air intake unit 70. 40 The discharge flow rate is approximately equal, so that the internal flow rate of the pipeline is kept stable, so as to facilitate the control of the desorption operation.
在本较佳实施例中,该催化剂氧化处理单元40还包括一洒水器130设于该第四管路44,该控制器120进一步电性连接该洒水器130。该洒水器130是用以补充水分至管路中以降低脱附气体的温度,否则若脱附气体温度过高,有可能使吸附材料失去活性或自燃。当然,如果第四管路44内的脱附气体可在第四管路44内迅速地自然散热而使吸附材料没有自燃的虞,则洒水器130也可以被省略或不作用。由于管路内补充了额外的水分,因此控制器120可进一步根据洒水器130的洒水量及进气单元70的进气量而相应地控制该排气单元80的排气量,使管路内的流量保持稳定。In this preferred embodiment, the catalyst oxidation treatment unit 40 further includes a sprinkler 130 disposed on the fourth pipeline 44 , and the controller 120 is further electrically connected to the sprinkler 130 . The sprinkler 130 is used to replenish water into the pipeline to reduce the temperature of the desorption gas, otherwise, if the temperature of the desorption gas is too high, the adsorption material may lose activity or spontaneously ignite. Of course, if the desorbed gas in the fourth pipeline 44 can quickly dissipate heat naturally in the fourth pipeline 44 so that the adsorption material does not have the risk of self-ignition, the sprinkler 130 can also be omitted or not function. Since additional water is supplemented in the pipeline, the controller 120 can further control the exhaust volume of the exhaust unit 80 according to the amount of water sprayed by the sprinkler 130 and the intake air volume of the air intake unit 70, so that the pipeline can flow remains stable.
在本较佳实施例中,为了精准地控制洒水器130的洒水量,催化剂氧化处理单元40还可包括一温度传感器140设于该第四管路44并位于该洒水器130与吸/脱附塔10a、10b之间而供感测管路内的气体温度,该控制器120电性连接于温度传感器140,并根据温度传感器140的讯号而控制洒水器130的洒水量,从而使脱附气体可被精准地降温至适当的工作温度。In this preferred embodiment, in order to accurately control the amount of water sprayed by the sprinkler 130, the catalyst oxidation treatment unit 40 may further include a temperature sensor 140 disposed in the fourth pipeline 44 and between the sprinkler 130 and the adsorption/desorption Between the towers 10a and 10b, the temperature of the gas in the pipeline is sensed. The controller 120 is electrically connected to the temperature sensor 140, and controls the amount of water sprayed by the sprinkler 130 according to the signal of the temperature sensor 140, so that the desorbed gas Can be precisely cooled down to the proper working temperature.
在前述实施例中,进气单元70及氧化气体传感器110是分别连通或设于第一管路41及第四管路44,惟两者的位置是可进行调整的,例如在图2所示的第二实施例中,进气单元70改连通于第二管路42,而氧化气体传感器110则改设于第三管路43,如此也能实现两者的设计目的。此外,在第二实施例中,吸附风车35改设于废气供给管路20,而脱附风车90则改设于第四管路44,同样可驱使气体在让管路内流动。为了进一步确保吸/脱附塔10a、10b不致因高温脱附气体而自燃,于吸/脱附塔10a、10b进气端前方还额外设有二温度传感器140a、140b,当温度传感器140a、140b感测脱附气体温度过高时,可启动吸/脱附塔10a、10b内部的洒水器(图未示)以进行降温。In the foregoing embodiments, the air intake unit 70 and the oxidizing gas sensor 110 are respectively communicated with or arranged on the first pipeline 41 and the fourth pipeline 44, but the positions of the two can be adjusted, as shown in FIG. 2 In the second embodiment, the intake unit 70 is connected to the second pipeline 42, and the oxidizing gas sensor 110 is connected to the third pipeline 43, so that the design objectives of the two can also be achieved. In addition, in the second embodiment, the adsorption windmill 35 is relocated to the exhaust gas supply pipeline 20, and the desorption windmill 90 is relocated to the fourth pipeline 44, which can also drive the gas to flow in the discharge pipeline. In order to further ensure that the adsorption/desorption towers 10a, 10b will not spontaneously ignite due to the high-temperature desorbed gas, two additional temperature sensors 140a, 140b are additionally arranged in front of the intake ends of the absorption/desorption towers 10a, 10b. When the temperature sensors 140a, 140b When it is sensed that the temperature of the desorption gas is too high, sprinklers (not shown) inside the absorption/desorption towers 10a, 10b can be activated to cool down.
需说明的是,前述各实施例的VOC处理装置虽仅包含二吸/脱附塔,惟实际上可依需求额外增加吸/脱附塔,这些吸/脱附塔可分别进行吸附作业、脱附作业或静置;在气体流量足够的环境或其他适当条件下,多个吸/脱附塔可以同时进行吸附作业,同样的,多个吸/脱附塔也可以同时进行脱附作业。It should be noted that although the VOC treatment devices in the foregoing embodiments only include two absorption/desorption towers, in fact, additional absorption/desorption towers can be added according to demand, and these absorption/desorption towers can respectively perform adsorption operations, desorption Adsorption operation or standing still; under the environment with sufficient gas flow or other appropriate conditions, multiple adsorption/desorption towers can perform adsorption operations at the same time, and similarly, multiple absorption/desorption towers can also perform desorption operations at the same time.
最后,必须再次说明的是,本实用新型于前述实施例中所揭示的构成组件仅为举例说明,并非用来限制本实用新型的范围,其他等效组件的替代或变化,亦应为本实用新型的申请专利范围所涵盖。Finally, it must be explained again that the constituent components disclosed in the foregoing embodiments of the present invention are only for illustration and are not intended to limit the scope of the present invention. The substitution or change of other equivalent components should also be included in the present invention. The scope of the new patent application is covered.
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| CN104772035A (en) * | 2014-01-15 | 2015-07-15 | 东虹工程股份有限公司 | Volatile organic compound processing device |
Families Citing this family (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN105536428A (en) * | 2015-12-14 | 2016-05-04 | 北京蓝博新科环保科技有限公司 | Organic waste gas purification system and purification method |
| CN119345851B (en) * | 2024-11-28 | 2025-12-30 | 中船(邯郸)派瑞特种气体股份有限公司 | A system and method for treating tail gas from tungsten hexafluoride synthesis. |
Family Cites Families (5)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| US6319484B1 (en) * | 1999-12-14 | 2001-11-20 | Engelhard Corporation | Compositions for abatement of volatile organic compounds and apparatus and methods using the same |
| JP5270912B2 (en) * | 2007-12-10 | 2013-08-21 | 中部電力株式会社 | Catalytic oxidation treatment apparatus and catalytic oxidation treatment method |
| CN102941000A (en) * | 2012-11-12 | 2013-02-27 | 天津市联合环保工程设计有限公司 | Organic waste gas multifunctional integral processing device |
| CN103394284B (en) * | 2013-06-04 | 2014-12-17 | 青岛华世洁环保科技有限公司 | Mobile enrichment-fixing catalytic oxidation type organic waste-gas treating apparatus |
| CN203990301U (en) * | 2014-01-15 | 2014-12-10 | 东虹工程股份有限公司 | Volatile organic compound processing device |
-
2014
- 2014-06-25 CN CN201420344061.5U patent/CN203990301U/en not_active Expired - Lifetime
- 2014-06-25 CN CN201410290249.0A patent/CN104772035B/en active Active
Cited By (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN104772035A (en) * | 2014-01-15 | 2015-07-15 | 东虹工程股份有限公司 | Volatile organic compound processing device |
| CN104772035B (en) * | 2014-01-15 | 2017-06-30 | 东虹工程股份有限公司 | Volatile organic compound processing device |
Also Published As
| Publication number | Publication date |
|---|---|
| CN104772035B (en) | 2017-06-30 |
| CN104772035A (en) | 2015-07-15 |
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