CN101480615A - Catalyst for decomposing laughing gas and preparation method thereof - Google Patents
Catalyst for decomposing laughing gas and preparation method thereof Download PDFInfo
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- CN101480615A CN101480615A CNA2009100797249A CN200910079724A CN101480615A CN 101480615 A CN101480615 A CN 101480615A CN A2009100797249 A CNA2009100797249 A CN A2009100797249A CN 200910079724 A CN200910079724 A CN 200910079724A CN 101480615 A CN101480615 A CN 101480615A
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- 239000003054 catalyst Substances 0.000 title claims abstract description 69
- GQPLMRYTRLFLPF-UHFFFAOYSA-N Nitrous Oxide Chemical compound [O-][N+]#N GQPLMRYTRLFLPF-UHFFFAOYSA-N 0.000 title claims abstract description 40
- 235000013842 nitrous oxide Nutrition 0.000 title claims abstract description 20
- 238000002360 preparation method Methods 0.000 title claims abstract description 7
- 239000003426 co-catalyst Substances 0.000 claims abstract description 11
- 229910052878 cordierite Inorganic materials 0.000 claims abstract description 10
- JSKIRARMQDRGJZ-UHFFFAOYSA-N dimagnesium dioxido-bis[(1-oxido-3-oxo-2,4,6,8,9-pentaoxa-1,3-disila-5,7-dialuminabicyclo[3.3.1]nonan-7-yl)oxy]silane Chemical compound [Mg++].[Mg++].[O-][Si]([O-])(O[Al]1O[Al]2O[Si](=O)O[Si]([O-])(O1)O2)O[Al]1O[Al]2O[Si](=O)O[Si]([O-])(O1)O2 JSKIRARMQDRGJZ-UHFFFAOYSA-N 0.000 claims abstract description 10
- 230000000694 effects Effects 0.000 claims abstract description 9
- 238000000034 method Methods 0.000 claims abstract description 8
- 238000005470 impregnation Methods 0.000 claims abstract description 3
- 229910044991 metal oxide Inorganic materials 0.000 claims abstract 4
- 150000004706 metal oxides Chemical class 0.000 claims abstract 4
- 229910052759 nickel Inorganic materials 0.000 claims abstract 2
- 229910052697 platinum Inorganic materials 0.000 claims abstract 2
- 238000001035 drying Methods 0.000 claims description 5
- 239000002245 particle Substances 0.000 claims description 5
- 238000007605 air drying Methods 0.000 claims description 4
- 239000011248 coating agent Substances 0.000 claims description 2
- 238000000576 coating method Methods 0.000 claims description 2
- 239000000470 constituent Substances 0.000 claims 10
- BASFCYQUMIYNBI-UHFFFAOYSA-N platinum Substances [Pt] BASFCYQUMIYNBI-UHFFFAOYSA-N 0.000 claims 2
- 239000002243 precursor Substances 0.000 claims 2
- 206010013786 Dry skin Diseases 0.000 claims 1
- 229910002651 NO3 Inorganic materials 0.000 claims 1
- NHNBFGGVMKEFGY-UHFFFAOYSA-N Nitrate Chemical compound [O-][N+]([O-])=O NHNBFGGVMKEFGY-UHFFFAOYSA-N 0.000 claims 1
- HPTLEXMXHIALNF-UHFFFAOYSA-L platinum(2+) dichlorate Chemical compound Cl(=O)(=O)[O-].[Pt+2].Cl(=O)(=O)[O-] HPTLEXMXHIALNF-UHFFFAOYSA-L 0.000 claims 1
- 238000010298 pulverizing process Methods 0.000 claims 1
- 238000012216 screening Methods 0.000 claims 1
- 239000007789 gas Substances 0.000 abstract description 22
- 239000002440 industrial waste Substances 0.000 abstract description 7
- 238000000354 decomposition reaction Methods 0.000 abstract description 5
- 239000012535 impurity Substances 0.000 abstract description 3
- PNEYBMLMFCGWSK-UHFFFAOYSA-N aluminium oxide Inorganic materials [O-2].[O-2].[O-2].[Al+3].[Al+3] PNEYBMLMFCGWSK-UHFFFAOYSA-N 0.000 abstract 1
- 229910052593 corundum Inorganic materials 0.000 abstract 1
- 231100000572 poisoning Toxicity 0.000 abstract 1
- 230000000607 poisoning effect Effects 0.000 abstract 1
- 229910001845 yogo sapphire Inorganic materials 0.000 abstract 1
- IJGRMHOSHXDMSA-UHFFFAOYSA-N Atomic nitrogen Chemical compound N#N IJGRMHOSHXDMSA-UHFFFAOYSA-N 0.000 description 22
- 239000000243 solution Substances 0.000 description 21
- YIXJRHPUWRPCBB-UHFFFAOYSA-N magnesium nitrate Chemical compound [Mg+2].[O-][N+]([O-])=O.[O-][N+]([O-])=O YIXJRHPUWRPCBB-UHFFFAOYSA-N 0.000 description 18
- UFMZWBIQTDUYBN-UHFFFAOYSA-N cobalt dinitrate Chemical compound [Co+2].[O-][N+]([O-])=O.[O-][N+]([O-])=O UFMZWBIQTDUYBN-UHFFFAOYSA-N 0.000 description 15
- 229910001981 cobalt nitrate Inorganic materials 0.000 description 15
- 238000006243 chemical reaction Methods 0.000 description 14
- MWUXSHHQAYIFBG-UHFFFAOYSA-N nitrogen oxide Inorganic materials O=[N] MWUXSHHQAYIFBG-UHFFFAOYSA-N 0.000 description 14
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 14
- 229910052757 nitrogen Inorganic materials 0.000 description 12
- KBJMLQFLOWQJNF-UHFFFAOYSA-N nickel(ii) nitrate Chemical compound [Ni+2].[O-][N+]([O-])=O.[O-][N+]([O-])=O KBJMLQFLOWQJNF-UHFFFAOYSA-N 0.000 description 11
- 239000012018 catalyst precursor Substances 0.000 description 10
- 239000012153 distilled water Substances 0.000 description 10
- 239000002253 acid Substances 0.000 description 9
- 229910018072 Al 2 O 3 Inorganic materials 0.000 description 7
- CURLTUGMZLYLDI-UHFFFAOYSA-N Carbon dioxide Chemical compound O=C=O CURLTUGMZLYLDI-UHFFFAOYSA-N 0.000 description 6
- 239000000203 mixture Substances 0.000 description 6
- 229910021094 Co(NO3)2-6H2O Inorganic materials 0.000 description 5
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 description 5
- 238000007654 immersion Methods 0.000 description 5
- 229910052760 oxygen Inorganic materials 0.000 description 5
- 239000001301 oxygen Substances 0.000 description 5
- QGZKDVFQNNGYKY-UHFFFAOYSA-N Ammonia Chemical compound N QGZKDVFQNNGYKY-UHFFFAOYSA-N 0.000 description 4
- 229910018590 Ni(NO3)2-6H2O Inorganic materials 0.000 description 4
- 238000005516 engineering process Methods 0.000 description 4
- 229930195733 hydrocarbon Natural products 0.000 description 4
- 229910019427 Mg(NO3)2-6H2O Inorganic materials 0.000 description 3
- 238000001354 calcination Methods 0.000 description 3
- 229910052799 carbon Inorganic materials 0.000 description 3
- 229910002092 carbon dioxide Inorganic materials 0.000 description 3
- 238000000746 purification Methods 0.000 description 3
- 238000010521 absorption reaction Methods 0.000 description 2
- 229910021529 ammonia Inorganic materials 0.000 description 2
- ZCCIPPOKBCJFDN-UHFFFAOYSA-N calcium nitrate Chemical compound [Ca+2].[O-][N+]([O-])=O.[O-][N+]([O-])=O ZCCIPPOKBCJFDN-UHFFFAOYSA-N 0.000 description 2
- 239000001569 carbon dioxide Substances 0.000 description 2
- 238000003421 catalytic decomposition reaction Methods 0.000 description 2
- 239000003638 chemical reducing agent Substances 0.000 description 2
- 150000002430 hydrocarbons Chemical class 0.000 description 2
- 238000009776 industrial production Methods 0.000 description 2
- 238000004519 manufacturing process Methods 0.000 description 2
- 239000007787 solid Substances 0.000 description 2
- 239000011949 solid catalyst Substances 0.000 description 2
- 239000000126 substance Substances 0.000 description 2
- 238000005406 washing Methods 0.000 description 2
- ONDPHDOFVYQSGI-UHFFFAOYSA-N zinc nitrate Chemical compound [Zn+2].[O-][N+]([O-])=O.[O-][N+]([O-])=O ONDPHDOFVYQSGI-UHFFFAOYSA-N 0.000 description 2
- MGWGWNFMUOTEHG-UHFFFAOYSA-N 4-(3,5-dimethylphenyl)-1,3-thiazol-2-amine Chemical compound CC1=CC(C)=CC(C=2N=C(N)SC=2)=C1 MGWGWNFMUOTEHG-UHFFFAOYSA-N 0.000 description 1
- 239000004215 Carbon black (E152) Substances 0.000 description 1
- UGFAIRIUMAVXCW-UHFFFAOYSA-N Carbon monoxide Chemical compound [O+]#[C-] UGFAIRIUMAVXCW-UHFFFAOYSA-N 0.000 description 1
- 241000282414 Homo sapiens Species 0.000 description 1
- CBENFWSGALASAD-UHFFFAOYSA-N Ozone Chemical compound [O-][O+]=O CBENFWSGALASAD-UHFFFAOYSA-N 0.000 description 1
- 239000011575 calcium Substances 0.000 description 1
- 238000010531 catalytic reduction reaction Methods 0.000 description 1
- 238000003912 environmental pollution Methods 0.000 description 1
- 239000003546 flue gas Substances 0.000 description 1
- 239000000446 fuel Substances 0.000 description 1
- 239000002737 fuel gas Substances 0.000 description 1
- 229910021472 group 8 element Inorganic materials 0.000 description 1
- 239000000463 material Substances 0.000 description 1
- VUZPPFZMUPKLLV-UHFFFAOYSA-N methane;hydrate Chemical compound C.O VUZPPFZMUPKLLV-UHFFFAOYSA-N 0.000 description 1
- -1 nitric oxide (NO) Chemical class 0.000 description 1
- JCXJVPUVTGWSNB-UHFFFAOYSA-N nitrogen dioxide Inorganic materials O=[N]=O JCXJVPUVTGWSNB-UHFFFAOYSA-N 0.000 description 1
- 230000009965 odorless effect Effects 0.000 description 1
- TWNQGVIAIRXVLR-UHFFFAOYSA-N oxo(oxoalumanyloxy)alumane Chemical group O=[Al]O[Al]=O TWNQGVIAIRXVLR-UHFFFAOYSA-N 0.000 description 1
- 239000002574 poison Substances 0.000 description 1
- 231100000614 poison Toxicity 0.000 description 1
- 230000002265 prevention Effects 0.000 description 1
- 238000000197 pyrolysis Methods 0.000 description 1
- 238000006722 reduction reaction Methods 0.000 description 1
- 239000012266 salt solution Substances 0.000 description 1
- 150000003839 salts Chemical class 0.000 description 1
- 239000002912 waste gas Substances 0.000 description 1
- 239000002699 waste material Substances 0.000 description 1
- 238000005303 weighing Methods 0.000 description 1
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Abstract
一种催化分解工业废气中笑气催化剂及其制备方法属于工业催化剂开发领域。现有催化剂对废气中的杂质敏感,易中毒失去活性,寿命短,价格昂贵。本发明提供的催化剂是负载型催化剂,以Al2O3或堇青石为载体、ⅡA、ⅡB、Ⅷ的一种或多种金属氧化物为活性组分,优选Ni和Pt作为主催化剂活性组分,优选Co和Mg作为助催化剂活性组分,主催化剂活性组分和助催化剂活性组分含量分别占催化剂的0.01~15.0%(wt)、0.0~20.0%(wt)。采用分步浸渍法制备催化剂,即载体先浸渍助催化剂活性组分、干燥后再浸渍主催化剂活性组分、干燥焙烧得到催化剂。本发明催化剂具有高效分解性、高稳定性和价格低廉等优点。A catalyst for catalytically decomposing laughing gas in industrial waste gas and a preparation method thereof belong to the field of industrial catalyst development. Existing catalysts are sensitive to impurities in exhaust gas, are prone to poisoning and lose activity, have short service life and are expensive. The catalyst provided by the invention is a supported catalyst, with Al2O3 or cordierite as the carrier, one or more metal oxides of IIA, IIB, and VIII as the active component , preferably Ni and Pt as the main catalyst active component , Co and Mg are preferably used as cocatalyst active components, and the content of the main catalyst active component and the cocatalyst active component accounts for 0.01-15.0% (wt) and 0.0-20.0% (wt) of the catalyst respectively. The catalyst is prepared by a step-by-step impregnation method, that is, the carrier is first impregnated with the active component of the co-catalyst, dried and then impregnated with the active component of the main catalyst, dried and calcined to obtain the catalyst. The catalyst of the invention has the advantages of high-efficiency decomposition, high stability, low price and the like.
Description
技术领域 technical field
本发明属于工业催化剂开发领域,具体涉及一种催化分解工业废气中笑气为氮气和氧气的负载型催化剂及其制备方法。The invention belongs to the field of industrial catalyst development, in particular to a supported catalyst for catalytically decomposing laughing gas in industrial waste gas into nitrogen and oxygen and a preparation method thereof.
背景技术 Background technique
随着经济的发展,人们对物质生活质量不断提高,化工产品的品种日益繁多,产品的质量不断提高,大工业化程度逐渐提高,而大工业化生产给环境造成的破坏日益严重,人类赖以生存的环境受到了严重破坏,保护环境、防止环境污染已经受到世界各国的高度重视,并积极采取行动保护人类赖以生存的环境。工业生产过程中的废气常常含有氮的氧化物,其中包括一氧化氮(NO)、二氧化氮(NO2)、笑气(N2O)。工业废气中NO、NO2可以采用水吸收的方法进行回收、利用达到净化处理目的。N2O是无色无嗅,化学性质稳定,不易被净化处理,以往一直缺乏成熟、有效的减排处理工艺技术,致使含有N2O的工业废气不经过任何处理而排向大气,而N2O是对地球大气层造成危害最为严重的气体之一,它在紫外线作用下与空气中氧反应形成光化学毒物、而且N2O严重的破坏臭氧层,同时又具有明显的温室效应,研究表明其温室效应是二氧化碳的300倍左右,因此控制和消除工业生产废气中的N2O向大中气排放已经引起世界各国的高度重视。并积极进行治理研究。目前对笑气处理技术主要有:With the development of the economy, people's material quality of life is constantly improving, the variety of chemical products is increasing, the quality of the products is constantly improving, and the degree of large-scale industrialization is gradually increasing. However, the damage caused by large-scale industrialized production to the environment is becoming more and more serious. The environment has been severely damaged, and the protection of the environment and the prevention of environmental pollution have been highly valued by countries all over the world, and they have taken active actions to protect the environment on which human beings live. Exhaust gases from industrial production processes often contain nitrogen oxides, including nitric oxide (NO), nitrogen dioxide (NO 2 ), and laughing gas (N 2 O). NO and NO 2 in industrial waste gas can be recovered and utilized by water absorption to achieve the purpose of purification treatment. N 2 O is colorless, odorless, stable in chemical properties, and not easy to be purified. In the past, there has been a lack of mature and effective emission reduction treatment technology, resulting in the industrial waste gas containing N 2 O being discharged into the atmosphere without any treatment, while N 2 O 2 O is one of the most harmful gases to the earth's atmosphere. It reacts with oxygen in the air to form photochemical poisons under the action of ultraviolet rays, and N 2 O seriously destroys the ozone layer. At the same time, it has an obvious greenhouse effect. Studies have shown that its greenhouse The effect of N 2 O is about 300 times that of carbon dioxide, so controlling and eliminating the emission of N 2 O in industrial production waste gas to large and medium-sized air has attracted great attention from all over the world. And actively conduct governance research. At present, the treatment technologies for laughing gas mainly include:
1、高温分解法1. Pyrolysis method
将N2O和含低碳烃类的燃料气一起送入高温反应炉中,在大于1000℃高温反应条件下,N2O和低碳烃类进行化学反应,其中N2O转化为氮气、烃类化合物则转化为二氧化碳和水(US 6328941;US 4973457;US 5429811;US 6056928),反应方程式如下所示:Send N 2 O and fuel gas containing low-carbon hydrocarbons together into a high-temperature reaction furnace. Under the high-temperature reaction conditions of more than 1000°C, N 2 O and low-carbon hydrocarbons undergo a chemical reaction, in which N 2 O is converted into nitrogen, Hydrocarbons are converted into carbon dioxide and water (US 6328941; US 4973457; US 5429811; US 6056928), and the reaction equation is as follows:
该技术净化工业废气中的N2O需要在高于1000℃的温度下进行,处理过程中消耗大量的烃类燃料,造成新的资源浪费;同时反应温度高,对设备的要求也非常苛刻,设备投资较高。The purification of N 2 O in industrial waste gas by this technology needs to be carried out at a temperature higher than 1000°C, and a large amount of hydrocarbon fuel is consumed in the process of treatment, resulting in waste of new resources; at the same time, the reaction temperature is high and the requirements for equipment are also very strict. Equipment investment is higher.
2、催化还原法2. Catalytic reduction method
在催化剂的作用下,通常在小于600℃的温度条件下,以氨为还原剂将氮氧化物转化为氮气和水(CN1660492;CN1903412;CN101011659;CN101028594;US 5736114),其代表性反应方程式为:Under the action of a catalyst, usually at a temperature of less than 600°C, ammonia is used as a reducing agent to convert nitrogen oxides into nitrogen and water (CN1660492; CN1903412; CN101011659; CN101028594; US 5736114), and the representative reaction equation is:
该技术在反应过程中需要添加还原剂如氨等,净化过程中操作条件严格,容易产生二次污染,而且催化剂对废气中的杂质要求严格,容易中毒失去活性,催化剂的稳定性差。This technology needs to add a reducing agent such as ammonia in the reaction process, and the operating conditions in the purification process are strict, which is prone to secondary pollution. Moreover, the catalyst has strict requirements on the impurities in the exhaust gas, is easy to be poisoned and loses activity, and the stability of the catalyst is poor.
3、催化分解法3. Catalytic decomposition method
通常在反应温度低于700℃的条件下,把笑气直接催化分解成氮气和氧气(CN1102435C;CN11088505C;CN120919C;WO9852681),其代表性反应方程式为:Usually, under the condition that the reaction temperature is lower than 700°C, laughing gas is directly catalytically decomposed into nitrogen and oxygen (CN1102435C; CN11088505C; CN120919C; WO9852681), and its representative reaction equation is:
该催化剂直接使N2O分解为氮气和氧气,催化剂对烟气中杂质含量要求严格,催化剂在高温条件下运行容易烧结,而失去活性,催化剂寿命短通常小于2年,催化剂的费用很高,使生产运行成本大幅度提高。The catalyst directly decomposes N 2 O into nitrogen and oxygen. The catalyst has strict requirements on the impurity content in the flue gas. The catalyst is easy to sinter under high temperature conditions and loses its activity. The life of the catalyst is usually less than 2 years, and the cost of the catalyst is very high. The cost of production operation is greatly increased.
发明内容 Contents of the invention
本发明的目的在于解决现有技术中的问题,提供一种净化工业废气,能够催化分解笑气的催化剂及其制备方法。The purpose of the present invention is to solve the problems in the prior art, and provide a catalyst for purifying industrial waste gas and capable of catalytically decomposing laughing gas and a preparation method thereof.
本发明提供的催化分解工业废气中笑气为氮气和氧气催化剂为负载型催化剂,其中载体是三氧化二铝或堇青石,催化剂活性组成为主催化剂活性组分和助催化剂活性组分,为IIA、IIB、VIII族元素中的一种或多种。主催化剂活性组分在催化剂中的质量含量为0.01~15.0%(wt)、助催化剂活性组分含量在催化剂中的质量含量为0.0~20.0%(wt)。The laughing gas in the catalytic decomposition of industrial waste gas provided by the present invention is nitrogen and oxygen. The catalyst is a supported catalyst, wherein the carrier is aluminum oxide or cordierite, and the active composition of the catalyst is the active component of the main catalyst and the active component of the co-catalyst, which is IIA , IIB, one or more of Group VIII elements. The mass content of the active component of the main catalyst in the catalyst is 0.01-15.0% (wt), and the content of the active component of the co-catalyst in the catalyst is 0.0-20.0% (wt).
本发明还提供了该固体催化剂的制备方法是采用分步浸渍法制备负载型固体催化剂,具体制备步骤如下:The present invention also provides that the preparation method of the solid catalyst is to prepare the supported solid catalyst by adopting step-by-step impregnation method, and the specific preparation steps are as follows:
1)首先测定干燥催化剂载体室温、常压条件下的吸水率。1) First measure the water absorption of the dry catalyst carrier at room temperature and normal pressure.
2)将主催化剂活性组分、助催化剂活性组分可溶性盐配制成一定浓度溶液。2) Prepare the active component of the main catalyst and the soluble salt of the active component of the co-catalyst into a certain concentration solution.
3)以Al2O3为载体时,载体一般需在600~800℃条件下进行培烧处理;以堇青石为载体时,堇青石需先粉碎、筛选得到40~60目颗粒,堇青石颗粒表面需进行Al2O3涂层预处理、干燥和焙烧后作为催化剂的载体。3) When Al 2 O 3 is used as the carrier, the carrier generally needs to be calcined at 600-800°C; when cordierite is used as the carrier, the cordierite needs to be pulverized and screened to obtain 40-60 mesh particles. The surface needs to be pretreated with Al 2 O 3 coating, dried and calcined as a catalyst carrier.
4)称(量)取定量的载体、助催化剂活性组分的盐溶液,进行助催化剂活性组分的浸渍,在室温条件下浸渍0.5~12.0小时后过滤,滤渣在95~120℃烘箱中鼓风干燥3~10小时后,再浸渍主催化剂活性组份0.1~1.0,在95~120℃烘箱中鼓风干燥3~10小时后,在500~600℃马福炉中老化2~4小时即得制备的催化剂。4) Weighing (quantity) take a quantitative amount of the carrier and the salt solution of the active component of the co-catalyst, impregnate the active component of the co-catalyst, filter after impregnating the active component of the co-catalyst for 0.5 to 12.0 hours at room temperature, and filter the filter residue in an oven at 95 to 120 ° C. After air-drying for 3-10 hours, impregnate the active component of the main catalyst with 0.1-1.0, air-dry in an oven at 95-120°C for 3-10 hours, then age in a muffle furnace at 500-600°C for 2-4 hours to prepare catalyst.
具体实施方式 Detailed ways
下面通过实施例详述本发明,但本发明并不限于下述的实施例。The present invention will be described in detail below through examples, but the present invention is not limited to the following examples.
实施例1Example 1
将堇青石(400孔/英寸2)研磨后筛选得到40~60目固体颗粒,进行洗涤预处理后在110℃条件下鼓风干燥3小时,浸渍Al2O3溶胶对载体进行修饰,在105℃条件下鼓风干燥10小时,650℃条件下焙烧2h得到催化剂载体。Cordierite (400 holes/inch 2 ) was ground and screened to obtain 40-60 mesh solid particles. After washing and pretreatment, it was air-dried at 110°C for 3 hours, and then impregnated with Al 2 O 3 sol to modify the carrier. The catalyst carrier was obtained by blast drying at ℃ for 10 hours and calcining at 650℃ for 2 hours.
称取硝酸钴[Co(NO3)2·6H2O]9.2g,溶解在200mL蒸馏水中,得到硝酸钴溶液;称取100g制备的载体,置于硝酸钴溶液中浸渍12.0小时后过滤,滤渣在110℃烘箱中鼓风干燥3小时得到催化剂前驱体I。Weigh 9.2 g of cobalt nitrate [Co(NO 3 ) 2 6H 2 O], dissolve it in 200 mL of distilled water to obtain a cobalt nitrate solution; weigh 100 g of the prepared carrier, put it in the cobalt nitrate solution and immerse it for 12.0 hours, then filter, and the filter residue The catalyst precursor I was obtained by air drying in an oven at 110° C. for 3 hours.
称取硝酸镍[Ni(NO3)2·6H2O]21.5g溶解在200mL蒸馏水中,得到硝酸镍溶液;将上述催化剂前驱体I置于硝酸镍溶液中0.5小时后过滤,滤渣在110℃烘箱中鼓风干燥5小时,在550℃马福炉中焙烧4小时,得到分解笑气催化剂I。Weigh 21.5 g of nickel nitrate [Ni(NO 3 ) 2 6H 2 O] and dissolve it in 200 mL of distilled water to obtain a nickel nitrate solution; place the above catalyst precursor I in the nickel nitrate solution for 0.5 hours and filter, and filter the residue at 110°C Blast drying in an oven for 5 hours, and roasting in a muffle furnace at 550° C. for 4 hours to obtain Catalyst I for Decomposing Laughing Gas.
称取1g制备的催化剂I置于固定床反应器中,在450℃、气体组成0.25%(v)N2O+氮气、气体体积空速2000mL/g.hr的实验条件下,N2O分解转化率为94.5%。Weigh 1g of the prepared catalyst I and place it in a fixed bed reactor. Under the experimental conditions of 450°C, gas composition 0.25% (v) N 2 O + nitrogen, and gas volume space velocity 2000mL/g.hr, N 2 O is decomposed and converted The rate is 94.5%.
实施例2Example 2
将堇青石(400孔/英寸2)研磨后筛选得到40~60目固体颗粒,进行洗涤预处理后在110℃条件下鼓风干燥3小时,浸渍Al2O3溶胶对载体进行修饰,在100℃条件下鼓风干燥4.5小时,600℃条件下焙烧2h得到催化剂载体。Cordierite (400 holes/ in2 ) was ground and screened to obtain 40-60 mesh solid particles. After washing and pretreatment, it was air-dried at 110°C for 3 hours, and then impregnated with Al 2 O 3 sol to modify the carrier. Blast drying at ℃ for 4.5 hours, and calcining at 600 ℃ for 2 hours to obtain a catalyst carrier.
称取硝酸钴[Co(NO3)2·6H2O]和[Ca(NO3)2·6H2O]10.0g和3.5g,溶解在200mL蒸馏水中,得到硝酸钴+硝酸钙溶液;称取的100g制备的载体,置于硝酸钴溶液中浸渍10小时后过滤,滤渣在并在95℃烘箱中鼓风干燥12小时得到催化剂前驱体II。Weigh cobalt nitrate [Co(NO 3 ) 2 6H 2 O] and [Ca(NO 3 ) 2 6H 2 O] 10.0g and 3.5g, dissolve in 200mL distilled water to obtain cobalt nitrate + calcium nitrate solution; weigh 100 g of the prepared carrier was taken, immersed in a cobalt nitrate solution for 10 hours, and then filtered, and the filter residue was air-dried in an oven at 95° C. for 12 hours to obtain the catalyst precursor II.
分别称取氯铂酸[H2PtCl6·6H2O]和硝酸镍[Ni(NO3)2·6H2O]2.5g和20.0g,溶解在200mL蒸馏水中,得到含硝酸镍和氯铂酸溶液,将催化剂前驱体II置于硝酸镍+氯铂酸溶液溶液中浸渍0.1小时后过滤,滤渣在100℃烘箱中鼓风干燥8小时,再在550℃马福炉中焙烧3小时,得到分解笑气催化剂II。Weigh 2.5g and 20.0g of chloroplatinic acid [H 2 PtCl 6 6H 2 O] and nickel nitrate [Ni(NO 3 ) 2 6H 2 O], respectively, and dissolve them in 200mL distilled water to obtain acid solution, the catalyst precursor II was placed in nickel nitrate + chloroplatinic acid solution for 0.1 hour and then filtered, and the filter residue was air-dried in an oven at 100°C for 8 hours, and then roasted in a muffle furnace at 550°C for 3 hours to obtain decomposed Gas Catalyst II.
称取1g制备的催化剂II于固定床反应器中,在450℃、气体组成0.25%(v)N2O+氮气、气体体积空速3000mL/g.hr的实验条件下,N2O分解转化率为99.8%。Weigh 1g of prepared catalyst II in a fixed bed reactor, under the experimental conditions of 450°C, gas composition 0.25% (v) N 2 O + nitrogen, gas volume space velocity 3000mL/g.hr, the decomposition conversion rate of N 2 O 99.8%.
实施例3Example 3
分别称取硝酸钴[Co(NO3)2·6H2O]、硝酸镁[Mg(NO3)2·6H2O]和硝酸鋅8.6g、10.4g和6.4g,溶解在200mL蒸馏水中,得到含硝酸钴和硝酸镁溶液;称取600℃培烧处理的Al2O3载体100g置于硝酸钴+硝酸镁溶液中,浸渍10小时后过滤,滤渣在95℃烘箱中鼓风干燥12小时,得到催化剂前驱体III;称取12.8g硝酸镍[Ni(NO3)2·6H2O],溶解在200mL蒸馏水中,得到硝酸镍溶液,将催化剂前驱体III置于硝酸镍溶液中浸渍2.0小时、过滤、滤渣在100℃干燥10小时,在550℃马福炉中焙烧3小时,得到分解笑气催化剂III。Weigh cobalt nitrate [Co(NO 3 ) 2 6H 2 O], magnesium nitrate [Mg(NO 3 ) 2 6H 2 O] and zinc nitrate 8.6g, 10.4g and 6.4g respectively, dissolve them in 200mL distilled water, Obtain a solution containing cobalt nitrate and magnesium nitrate; weigh 100g of the Al 2 O 3 carrier that has been calcined at 600°C and place it in the cobalt nitrate+magnesium nitrate solution, filter after immersion for 10 hours, and dry the filter residue in an oven at 95°C for 12 hours , to obtain the catalyst precursor III; weigh 12.8g of nickel nitrate [Ni(NO 3 ) 2 6H 2 O], dissolve it in 200mL of distilled water to obtain a nickel nitrate solution, and place the catalyst precursor III in the nickel nitrate solution for 2.0 hours, filtered, and the filter residue was dried at 100° C. for 10 hours, and calcined in a muffle furnace at 550° C. for 3 hours to obtain catalyst III for decomposing laughing gas.
称取1g制备的催化剂III于固定床反应装置中,在300℃、气体体积组成1.35%(v)N2O+1.8%(v)O2+1.01%(v)CO+3.5%(v)CO2+0.02%(v)NO+0.01%(v)NO2+2.5%(v)H2O+0.03%(v)SO2+氮气、气体体积空速2000mL/g.hr的实验条件下,N2O分解转化率为69.8%。Weigh 1g of prepared catalyst III in a fixed bed reaction device, at 300°C, gas volume composition 1.35% (v) N 2 O + 1.8% (v) O 2 + 1.01% (v) CO + 3.5% (v) Under the experimental conditions of CO 2 +0.02%(v)NO+0.01%(v)NO 2 +2.5%(v)H 2 O+0.03%(v)SO 2 +nitrogen, gas volume space velocity 2000mL/g.hr , N 2 O decomposition conversion rate was 69.8%.
实施例4Example 4
分别称取硝酸钴[Co(NO3)2·6H2O]和硝酸镁[Mg(NO3)2·6H2O]10.3g和10.4g,溶解在200mL蒸馏水中,得到得到含硝酸钴和硝酸镁溶液;称取650℃培烧处理Al2O3载体100g置于硝酸钴+硝酸镁溶液中,浸渍0.5小时后过滤,滤渣在95℃烘箱中鼓风干燥12小时,得到催化剂前驱体IV。Weigh cobalt nitrate [Co(NO 3 ) 2 6H 2 O] and magnesium nitrate [Mg(NO 3 ) 2 6H 2 O] 10.3g and 10.4g respectively, and dissolve them in 200mL distilled water to obtain cobalt nitrate and Magnesium nitrate solution; Weigh 100g of Al 2 O 3 carrier that has been calcined at 650°C, place it in cobalt nitrate + magnesium nitrate solution, filter after immersion for 0.5 hours, and dry the filter residue in an oven at 95°C for 12 hours to obtain catalyst precursor IV .
称取2.2g氯铂酸[H2PtCl6·6H2O]溶解在200mL蒸馏水中,得到氯铂酸溶液;将催化剂前驱体VI置于氯铂酸溶液中,浸渍0.1小时后过滤,滤渣在105℃烘箱中鼓风干燥10小时,再在550℃马福炉中焙烧3小时,得到分解笑气催化剂IV。Weigh 2.2g of chloroplatinic acid [H 2 PtCl 6 6H 2 O] and dissolve it in 200mL of distilled water to obtain a chloroplatinic acid solution; place the catalyst precursor VI in the chloroplatinic acid solution, filter after immersion for 0.1 hour, and filter residue in Blast drying in an oven at 105°C for 10 hours, and then calcining in a muffle furnace at 550°C for 3 hours to obtain catalyst IV for decomposing laughing gas.
称取1g催化剂IV,在300℃、气体体积组成1.35%(v)N2O+1.8%(v)O2+1.01%(v)CO+3.5%(v)CO2+0.02%(v)NO+0.01%(v)NO2+2.5%(v)H2O+0.03%(v)SO2+氮气、气体体积空速2000mL/g.hr的实验条件下,N2O分解转化率为73.7%。Weigh 1g of catalyst IV, at 300°C, the gas volume composition is 1.35%(v) N2O +1.8%(v) O2 +1.01%(v)CO+3.5%(v) CO2 +0.02%(v) Under the experimental conditions of NO+0.01%(v)NO 2 +2.5%(v)H 2 O+0.03%(v)SO 2 +nitrogen, gas volume space velocity 2000mL/g.hr, the decomposition conversion rate of N 2 O is 73.7%.
实施例5Example 5
分别称取硝酸钴[Co(NO3)2·6H2O]和硝酸镁[Mg(NO3)2·6H2O]7.1g和5.7g,溶解在200mL蒸馏水中,得到得到含硝酸钴和硝酸镁溶液;称取650℃培烧处理的Al2O3载体100g置于硝酸钴+硝酸镁溶液中,浸渍2.0小时后过滤,滤渣在105℃烘箱中鼓风干燥5小时,得到催化剂前驱体V;Weigh cobalt nitrate [Co(NO 3 ) 2 6H 2 O] and magnesium nitrate [Mg(NO 3 ) 2 6H 2 O] 7.1g and 5.7g respectively, and dissolve them in 200mL distilled water to obtain cobalt nitrate and Magnesium nitrate solution; Weigh 100g of the Al 2 O 3 carrier that has been calcined at 650°C and place it in cobalt nitrate+magnesium nitrate solution, filter after immersion for 2.0 hours, and dry the filter residue in an oven at 105°C for 5 hours to obtain a catalyst precursor V;
分别称取氯铂酸[H2PtCl6·6H2O]和硝酸镍[Ni(NO3)2·6H2O]1.1g和15.0g溶解在200mL蒸馏水中,得到氯铂酸+硝酸镍溶液;将催化剂前驱体V置于氯铂酸+硝酸镍溶液中,浸渍2.0小时后过滤,滤渣在105℃烘箱中鼓风干燥5小时,再在600℃马福炉中焙烧3小时,得到分解笑气催化剂V。Weigh 1.1g and 15.0g of chloroplatinic acid [H 2 PtCl 6 6H 2 O] and nickel nitrate [Ni(NO 3 ) 2 6H 2 O] respectively and dissolve them in 200mL distilled water to obtain chloroplatinic acid + nickel nitrate solution The catalyst precursor V was placed in chloroplatinic acid+nickel nitrate solution, filtered after immersion for 2.0 hours, and the filter residue was air-dried in an oven at 105°C for 5 hours, and then roasted in a muffle furnace at 600°C for 3 hours to obtain a catalyst for decomposing laughing gas V.
称取1g催化剂V,在400℃、气体体积组成1.35%(v)N2O+1.8%(v)O2+1.01%(v)CO+3.5%(v)CO2+0.02%(v)NO+0.01%(v)NO2+2.5%(v)H2O+0.03%(v)SO2+氮气、气体体积空速2000mL/g.hr的实验条件下,N2O分解转化率为98.9%。Weigh 1g of catalyst V, at 400°C, the gas volume composition is 1.35%(v)N 2 O+1.8%(v)O 2 +1.01%(v)CO+3.5%(v)CO 2 +0.02%(v) Under the experimental conditions of NO+0.01%(v)NO 2 +2.5%(v)H 2 O+0.03%(v)SO 2 +nitrogen, gas volume space velocity 2000mL/g.hr, the decomposition conversion rate of N 2 O is 98.9%.
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Cited By (4)
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---|---|---|---|---|
CN102451683A (en) * | 2010-10-27 | 2012-05-16 | 中国科学院大连化学物理研究所 | Noble metal catalyst and preparation and application thereof |
CN102513127A (en) * | 2011-11-21 | 2012-06-27 | 张远洋 | Nitrogen monoxide catalyst with deep ammonia reduction function and preparation method thereof |
CN105363451A (en) * | 2015-12-04 | 2016-03-02 | 中国天辰工程有限公司 | Efficient catalyst for decomposition of N2O and preparation method and application thereof |
CN106076112A (en) * | 2016-06-03 | 2016-11-09 | 阳煤集团深州化工有限公司 | One removes N simultaneously2o and NOxmethod |
-
2009
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Non-Patent Citations (2)
Title |
---|
化学化工大辞典编委会: "《化学化工大辞典》", 31 January 2003 * |
陈敬中: "《现代晶体化学-理论与方法》", 31 December 2001 * |
Cited By (5)
Publication number | Priority date | Publication date | Assignee | Title |
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CN102451683A (en) * | 2010-10-27 | 2012-05-16 | 中国科学院大连化学物理研究所 | Noble metal catalyst and preparation and application thereof |
CN102513127A (en) * | 2011-11-21 | 2012-06-27 | 张远洋 | Nitrogen monoxide catalyst with deep ammonia reduction function and preparation method thereof |
CN105363451A (en) * | 2015-12-04 | 2016-03-02 | 中国天辰工程有限公司 | Efficient catalyst for decomposition of N2O and preparation method and application thereof |
CN105363451B (en) * | 2015-12-04 | 2018-01-26 | 中国天辰工程有限公司 | One kind is used to decompose N2O effective catalyst and its preparation method and application |
CN106076112A (en) * | 2016-06-03 | 2016-11-09 | 阳煤集团深州化工有限公司 | One removes N simultaneously2o and NOxmethod |
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