CN113713851B - Preparation method of In/H-beta catalyst for improving sulfur resistance and water resistance - Google Patents

Preparation method of In/H-beta catalyst for improving sulfur resistance and water resistance Download PDF

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CN113713851B
CN113713851B CN202111144477.3A CN202111144477A CN113713851B CN 113713851 B CN113713851 B CN 113713851B CN 202111144477 A CN202111144477 A CN 202111144477A CN 113713851 B CN113713851 B CN 113713851B
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CN113713851A (en
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朱荣淑
洪梅
赵玖虎
董磊
朱满玉
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Peking University Shenzhen Graduate School
Harbin Institute of Technology Shenzhen
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    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J29/00Catalysts comprising molecular sieves
    • B01J29/04Catalysts comprising molecular sieves having base-exchange properties, e.g. crystalline zeolites
    • B01J29/06Crystalline aluminosilicate zeolites; Isomorphous compounds thereof
    • B01J29/70Crystalline aluminosilicate zeolites; Isomorphous compounds thereof of types characterised by their specific structure not provided for in groups B01J29/08 - B01J29/65
    • B01J29/7049Crystalline aluminosilicate zeolites; Isomorphous compounds thereof of types characterised by their specific structure not provided for in groups B01J29/08 - B01J29/65 containing rare earth elements, titanium, zirconium, hafnium, zinc, cadmium, mercury, gallium, indium, thallium, tin or lead
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    • B01J2229/00Aspects of molecular sieve catalysts not covered by B01J29/00
    • B01J2229/10After treatment, characterised by the effect to be obtained
    • B01J2229/18After treatment, characterised by the effect to be obtained to introduce other elements into or onto the molecular sieve itself
    • B01J2229/186After treatment, characterised by the effect to be obtained to introduce other elements into or onto the molecular sieve itself not in framework positions

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Abstract

The invention discloses a preparation method of an In-H/beta catalyst for improving sulfur resistance and water resistance. The preparation method comprises the following steps: mixing raw materials comprising amino acid, a silicon source, an aluminum source, an M source, an organic amine template agent and water for reaction to obtain reaction gel; crystallizing the reaction gel to obtain an M-beta molecular sieve; mixing with ammonium salt solution, and ion exchanging to obtain H-beta molecular sieve; step 4: mixing the H-beta molecular sieve with indium salt solution, and obtaining the In/H-beta molecular sieve after ion exchange. The amino acid can promote crystallization In the preparation process as a guiding agent, and can lead the finally prepared In/H-beta catalyst to obtain strongerAcid active center, thus can be in SO 2 And H 2 Under O interference, the best CH is shown 4 SCR catalytic activity and cycle performance.

Description

一种提高抗硫抗水性能的In/H-β催化剂制备方法A preparation method for In/H-β catalyst that improves sulfur and water resistance

技术领域Technical field

本申请涉及选择性催化还原脱硝技术领域,尤其是涉及一种提高抗硫抗水性能的In-H/β催化剂制备方法。The present application relates to the technical field of selective catalytic reduction denitration, and in particular to a preparation method of In-H/β catalyst that improves sulfur and water resistance.

背景技术Background technique

化石燃料燃烧排放的氮氧化物(NOx)不仅会对人类呼吸系统造成损害,而且还会造成光化学烟雾、酸雨和其他一些严重的环境问题。对此,研究人员提出了一系列的解决方案,而选择性催化还原(SCR)脱硝目前被认为是将NOx转化为N2从而解决NOx排放的最佳方法,其中CH4是天然气的主要成分,储量丰富、完全民用化且价格低廉,是NOx去除技术中最具前景的技术。Nitrogen oxides ( NOx ) emitted by the combustion of fossil fuels not only cause damage to the human respiratory system, but also cause photochemical smog, acid rain and other serious environmental problems. In this regard, researchers have proposed a series of solutions, and selective catalytic reduction (SCR) denitrification is currently considered the best way to convert NO x into N 2 to solve NO x emissions, of which CH 4 is the main component of natural gas. Composition, abundant reserves, complete civilian use and low price, it is the most promising technology among NO x removal technologies.

高效催化剂的开发对于CH4-SCR技术的商业化具有重要意义。沸石基催化剂因其较高的内表面积、均匀的微孔系统、可观的离子交换能力和较高的热稳定性而越来越受到人们的关注。β分子筛具有三维12元环通道,孔径为0.55×0.55nm和0.76×0.64nm,是SCR应用中最重要的沸石骨架之一,可作为有效的催化剂载体。通常将金属或金属氧化物并入沸石框架中以进一步提高其催化性能。Pan等人发现,采用铟盐浸渍法制备的In/H-β催化剂在CH4-SCR系统中具有较高的催化性能。而我们课题组进一步对制备条件的优化,也可以制备出更高活性In/H-β催化剂。The development of efficient catalysts is of great significance for the commercialization of CH 4 -SCR technology. Zeolite-based catalysts have attracted increasing attention due to their high internal surface area, uniform micropore system, considerable ion exchange capacity, and high thermal stability. Beta molecular sieve has three-dimensional 12-membered ring channels with pore sizes of 0.55×0.55nm and 0.76×0.64nm. It is one of the most important zeolite frameworks in SCR applications and can be used as an effective catalyst carrier. Metals or metal oxides are often incorporated into the zeolite framework to further enhance its catalytic performance. Pan et al. found that the In/H-β catalyst prepared by the indium salt impregnation method has higher catalytic performance in the CH 4 -SCR system. By further optimizing the preparation conditions, our research group can also prepare a more active In/H-β catalyst.

然而,在工业应用中,除了考虑催化剂本身的催化性能外,还需要考虑SO2以及高浓度水汽这些干扰SCR过程的因素。实验过程中发现,目前的In/H-β催化剂对二氧化硫和水蒸气的耐受性仍有待提高。在没有SO2和H2O的情况下,NOx去除效率可以达到90%以上,但在原料蒸汽中加入100ppm SO2和5vol.%H2O后,NOx去除效率剧烈下降(仅约10%)。因此,有必要通过对制备方法的改进来提高In/H-β催化剂在SO2和H2O存在下的催化性能。However, in industrial applications, in addition to considering the catalytic performance of the catalyst itself, factors such as SO 2 and high concentrations of water vapor that interfere with the SCR process also need to be considered. During the experiment, it was found that the current In/H-β catalyst’s tolerance to sulfur dioxide and water vapor still needs to be improved. In the absence of SO 2 and H 2 O, the NO x removal efficiency can reach more than 90%, but after adding 100 ppm SO 2 and 5vol.% H 2 O to the raw steam, the NO x removal efficiency drops sharply (only about 10 %). Therefore, it is necessary to improve the catalytic performance of In/H-β catalyst in the presence of SO 2 and H 2 O by improving the preparation method.

发明内容Contents of the invention

本申请旨在至少解决现有技术中存在的技术问题之一。为此,本申请提出一种在SO2和H2O存在下仍然具有良好的CH4-SCR催化性能的In/H-β催化剂的制备方法。This application aims to solve at least one of the technical problems existing in the prior art. To this end, this application proposes a preparation method for an In/H-β catalyst that still has good CH 4 -SCR catalytic performance in the presence of SO 2 and H 2 O.

本申请的第一方面,提供In/H-β催化剂的制备方法,该制备方法包括以下步骤:The first aspect of this application provides a preparation method of In/H-β catalyst, which preparation method includes the following steps:

步骤1:取包括氨基酸、硅源、铝源、M源、有机胺模板剂、水的原料混合反应,得到反应凝胶;Step 1: Mix and react raw materials including amino acids, silicon sources, aluminum sources, M sources, organic amine templates, and water to obtain a reaction gel;

步骤2:将反应凝胶晶化,冷却后洗涤、干燥、焙烧,得到M-β分子筛;Step 2: Crystallize the reaction gel, cool, wash, dry and roast to obtain M-β molecular sieve;

步骤3:将M-β分子筛与铵盐溶液混合反应,完成离子交换后洗涤、干燥、焙烧,得到H-β分子筛;Step 3: Mix and react M-β molecular sieve with ammonium salt solution, complete ion exchange, wash, dry and roast to obtain H-β molecular sieve;

步骤4:将H-β分子筛与铟盐溶液混合反应,完成离子交换后洗涤、干燥、焙烧,得到In/H-β分子筛;Step 4: Mix and react H-β molecular sieve with indium salt solution, complete ion exchange, wash, dry and roast to obtain In/H-β molecular sieve;

其中,M为碱金属、碱土金属中的至少一种。Wherein, M is at least one of an alkali metal and an alkaline earth metal.

根据本申请实施例的制备方法,至少具有如下有益效果:The preparation method according to the embodiment of the present application has at least the following beneficial effects:

氨基酸作为导引剂在制备过程中会促进结晶,并使得最终制得的In/H-β催化剂能够获得较强的酸活性中心,从而能够在SO2和H2O干扰下,表现出最佳的CH4-SCR催化活性和循环性能。As a guiding agent, amino acids will promote crystallization during the preparation process and enable the final In/H-β catalyst to obtain stronger Acid active center, thus able to show the best CH4 -SCR catalytic activity and cycle performance under the interference of SO2 and H2O .

在本申请的一些实施方式中,硅源以二氧化硅计,氨基酸/二氧化硅的摩尔比值为0.1~0.5。进一步,脯氨酸/二氧化硅的摩尔比值优选为0.15~0.45,进一步优选为0.2~0.4,进一步优选为0.3。In some embodiments of the present application, the silicon source is calculated as silica, and the molar ratio of amino acid/silica is 0.1 to 0.5. Furthermore, the molar ratio of proline/silica is preferably 0.15 to 0.45, more preferably 0.2 to 0.4, and even more preferably 0.3.

在本申请的一些实施方式中,铝源、M源以氧化物计,有机胺模板剂以季铵离子计,二氧化硅/氧化铝的摩尔比值为5~200,氧化M/二氧化硅的摩尔比值为0.01~0.4,季铵离子/二氧化硅的摩尔比值为0.1~0.8。In some embodiments of the present application, the aluminum source and M source are calculated as oxides, the organic amine template is calculated as quaternary ammonium ions, the molar ratio of silicon dioxide/alumina is 5 to 200, and the molar ratio of M oxide/silica is The molar ratio is 0.01 to 0.4, and the molar ratio of quaternary ammonium ions/silica is 0.1 to 0.8.

在本申请的一些实施方式中,水/二氧化硅的摩尔比值为5~50。In some embodiments of the present application, the molar ratio of water/silica is 5-50.

在本申请的一些实施方式中,氨基酸选自脯氨酸、丙氨酸、谷氨酸、组氨酸、丝氨酸、精氨酸中得至少一种。In some embodiments of the present application, the amino acid is selected from at least one of proline, alanine, glutamic acid, histidine, serine, and arginine.

在本申请的一些实施方式中,氨基酸为脯氨酸。In some embodiments of the present application, the amino acid is proline.

氨基酸作为导引剂在制备过程中会促进结晶,同时在β分子筛中生成一定数量的介孔,这些介孔的存在会促进反应物和产物的扩散从而提高催化性能。但发明人在进一步实验过程中发现,In/H-β催化剂对二氧化硫和水蒸气的耐受性并不仅仅受限于介孔这一因素,还与其他理化性质有关。相较于其它氨基酸,脯氨酸独特的环状侧链使得最终制备得到的In/H-β催化剂能够获得更强的酸活性中心,从而能够在SO2和H2O干扰下,表现出最佳的CH4-SCR催化活性和循环性能。As a guide agent, amino acids will promote crystallization during the preparation process and generate a certain number of mesopores in the β molecular sieve. The existence of these mesopores will promote the diffusion of reactants and products and thereby improve the catalytic performance. However, during further experiments, the inventor found that the tolerance of the In/H-β catalyst to sulfur dioxide and water vapor is not only limited by the factor of mesopores, but is also related to other physical and chemical properties. Compared with other amino acids, the unique cyclic side chain of proline enables the final prepared In/H-β catalyst to obtain stronger Acid active center, thus able to show the best CH4 -SCR catalytic activity and cycle performance under the interference of SO2 and H2O .

在本申请的一些实施方式中,硅源选自白炭黑、水玻璃、正硅酸乙酯、硅溶胶、硅凝胶和固体硅胶中的至少一种。In some embodiments of the present application, the silicon source is selected from at least one of white carbon black, water glass, ethyl orthosilicate, silica sol, silica gel and solid silica gel.

在本申请的一些实施方式中,铝源选自铝盐、铝酸盐、偏铝酸盐、氢氧化铝、拟薄水铝石、仲丁醇铝、异丙醇铝中的至少一种。In some embodiments of the present application, the aluminum source is selected from at least one of aluminum salts, aluminates, metaaluminates, aluminum hydroxide, pseudoboehmite, aluminum sec-butoxide, and aluminum isopropoxide.

在本申请的一些实施方式中,M选自锂、钠、钾、铯、锶、钙、钡中的至少一种。In some embodiments of the present application, M is selected from at least one of lithium, sodium, potassium, cesium, strontium, calcium, and barium.

在本申请的一些实施方式中,M源选自M的碱、盐中的至少一种,包括但不限于氢氧化钠、氢氧化钾、氯化钠、氯化钾等。In some embodiments of the present application, the source of M is selected from at least one of bases and salts of M, including but not limited to sodium hydroxide, potassium hydroxide, sodium chloride, potassium chloride, etc.

在本申请的一些实施方式中,有机胺模板剂选自二乙胺、三乙胺、吗啡啉、四乙基氢氧化铵、四乙基氯化铵、四乙基溴化铵、四乙基碘化铵等其中的至少一种。In some embodiments of the present application, the organic amine template is selected from diethylamine, triethylamine, morpholine, tetraethylammonium hydroxide, tetraethylammonium chloride, tetraethylammonium bromide, tetraethylammonium At least one of ammonium iodide and the like.

在本申请的一些实施方式中,铟盐溶液中铟离子的浓度为0.01~0.1mol/L。In some embodiments of the present application, the concentration of indium ions in the indium salt solution is 0.01 to 0.1 mol/L.

在本申请的一些实施方式中,步骤2中反应凝胶的晶化温度为100~220℃,晶化时间为5~200小时。In some embodiments of the present application, the crystallization temperature of the reaction gel in step 2 is 100-220°C, and the crystallization time is 5-200 hours.

在本申请的一些实施方式中,步骤3~4中离子交换反应的反应温度为70~100℃,反应时间为20min~12h。In some embodiments of the present application, the reaction temperature of the ion exchange reaction in steps 3 to 4 is 70 to 100°C, and the reaction time is 20 min to 12 hours.

在本申请的一些实施方式中,步骤3中离子交换反应、洗涤、干燥重复1~3次后进行焙烧。In some embodiments of the present application, in step 3, the ion exchange reaction, washing, and drying are repeated 1 to 3 times and then roasted.

在本申请的一些实施方式中,步骤2~4中焙烧温度为400~600℃,焙烧时间为1~6h。In some embodiments of the present application, the calcining temperature in steps 2 to 4 is 400 to 600°C, and the calcining time is 1 to 6 hours.

在本申请的一些实施方式中,步骤2~4中干燥温度为60~150℃,干燥时间为1~24h。In some embodiments of the present application, the drying temperature in steps 2 to 4 is 60 to 150°C, and the drying time is 1 to 24 hours.

本申请的第二方面,提供一种In/H-β催化剂,该In/H-β催化剂采用前述的制备方法制得。The second aspect of this application provides an In/H-β catalyst, which is prepared by the aforementioned preparation method.

本申请的第三方面,提供一种In/H-β催化剂,该In/H-β催化剂酸位点的浓度为50μmol/g以上。优选的,/>酸位点的浓度为60μmol/g以上、70μmol/g以上、80μmol/g以上、90μmol/g以上、100μmol/g以上、110μmol/g以上、120μmol/g以上。/>酸位点的浓度由积分摩尔消光系数(IMEC)计算得到。The third aspect of the present application provides an In/H-β catalyst. The In/H-β catalyst The concentration of acid sites is 50 μmol/g or more. Preferred,/> The concentration of the acid site is 60 μmol/g or more, 70 μmol/g or more, 80 μmol/g or more, 90 μmol/g or more, 100 μmol/g or more, 110 μmol/g or more, or 120 μmol/g or more. /> The concentration of acid sites was calculated from the integrated molar extinction coefficient (IMEC).

在本申请的一些实施方式中,酸位点/Lewis酸位点的浓度比值为0.55以上。优选的,/>酸/Lewis酸的比值为0.6以上、0.65以上、0.7以上、0.72以上。Lewis酸位点的浓度同样由积分摩尔消光系数(IMEC)计算得到。In some embodiments of the present application, The concentration ratio of acid sites/Lewis acid sites is above 0.55. Preferred,/> The ratio of acid/Lewis acid is 0.6 or more, 0.65 or more, 0.7 or more, or 0.72 or more. The concentration of Lewis acid sites is also calculated from the integrated molar extinction coefficient (IMEC).

在本申请的一些实施方式中,Lewis酸位点的浓度为140μmol/g以上。优选的,Lewis酸位点的浓度为145μmol/g以上、150μmol/g以上、155μmol/g以上、160μmol/g以上、165μmol/g以上。In some embodiments of the present application, the concentration of Lewis acid sites is above 140 μmol/g. Preferably, the concentration of Lewis acid sites is 145 μmol/g or more, 150 μmol/g or more, 155 μmol/g or more, 160 μmol/g or more, or 165 μmol/g or more.

在本申请的一些实施方式中,该In/H-β催化剂具有80%以上的甲烷选择性(检测条件:原料气含有400ppm NO、400ppm CH4、10vol.%O2、100ppm SO2、5vol.%H2O,其余为Ar作为平衡气体,流速为100mL/min,空速23600h-1,程序升温速率4℃/min(100-650℃),催化剂用量100mg)。进一步甲烷选择性在85%以上、90%以上、95%以上、98%以上、99%以上。In some embodiments of the application, the In/H-β catalyst has a methane selectivity of more than 80% (detection conditions: the feed gas contains 400ppm NO, 400ppm CH 4 , 10vol.% O 2 , 100ppm SO 2 , 5vol. %H 2 O, the rest is Ar as the balance gas, the flow rate is 100mL/min, the space velocity is 23600h -1 , the programmed temperature rise rate is 4℃/min (100-650℃), the catalyst dosage is 100mg). Furthermore, the methane selectivity is above 85%, above 90%, above 95%, above 98%, above 99%.

在本申请的一些实施方式中,该In/H-β催化剂在原料气含有400ppm NO、400ppmCH4、10vol.%O2、100ppm SO2、5vol.%H2O,其余为Ar作为平衡气体,流速为100mL/min,空速23600h-1,程序升温速率4℃/min(100-650℃),催化剂用量100mg的检测条件下,具有30%以上、35%以上、38%以上、40%以上的氮氧化物去除率。并且在三次循环后,在650℃下仍然有30%以上、35%以上、36%以上、37%以上的氮氧化物去除率。In some embodiments of the application, the In/H-β catalyst contains 400ppm NO, 400ppmCH 4 , 10vol.% O 2 , 100ppm SO 2 , 5vol.% H 2 O in the feed gas, and the rest is Ar as a balance gas, Under the testing conditions of flow rate 100mL/min, space velocity 23600h -1 , programmed heating rate 4℃/min (100-650℃), and catalyst dosage 100mg, the performance is more than 30%, more than 35%, more than 38%, more than 40%. nitrogen oxide removal rate. And after three cycles, there are still nitrogen oxide removal rates of more than 30%, more than 35%, more than 36%, and more than 37% at 650°C.

在本申请的一些实施方式中,In/H-β催化剂包括H-β分子筛载体和负载于H-β分子筛载体上的铟。更具体的,铟均匀分布在H-β分子筛载体的表面和内部。In some embodiments of the present application, the In/H-β catalyst includes an H-β molecular sieve carrier and indium supported on the H-β molecular sieve carrier. More specifically, indium is evenly distributed on the surface and inside of the H-β molecular sieve carrier.

在本申请的一些实施方式中,In/H-β催化剂中铟的含量为In/H-β催化剂总质量的2~8wt%。优选的,铟含量在3wt%以上、3.5wt%以上、4wt%以上、4.5wt%以上、5wt%以上。优选的,铟含量在7.5wt%以下、7.4wt%以下、7.3wt%以下、7.2wt%以下、7.1wt%以下。In some embodiments of the present application, the content of indium in the In/H-β catalyst is 2 to 8 wt% of the total mass of the In/H-β catalyst. Preferably, the indium content is above 3wt%, above 3.5wt%, above 4wt%, above 4.5wt%, or above 5wt%. Preferably, the indium content is below 7.5 wt%, below 7.4 wt%, below 7.3 wt%, below 7.2 wt%, or below 7.1 wt%.

在本申请的一些实施方式中,In/H-β催化剂中Si/Al摩尔比为25以上。In some embodiments of the present application, the Si/Al molar ratio in the In/H-β catalyst is above 25.

在本申请的一些实施方式中,In/H-β催化剂中In/Al摩尔比为0.7以上。优选为0.71以上、0.72以上、0.73以上、0.74以上、0.75以上、0.76以上、0.77以上、0.78以上、0.79以上、0.8以上。In some embodiments of the present application, the In/Al molar ratio in the In/H-β catalyst is above 0.7. Preferably it is 0.71 or more, 0.72 or more, 0.73 or more, 0.74 or more, 0.75 or more, 0.76 or more, 0.77 or more, 0.78 or more, 0.79 or more, and 0.8 or more.

本申请的第四方面,提供一种脱硝方法,该脱硝方法采用选择性催化还原法对废气进行处理,以CH4为还原剂,催化剂选用前述的In/H-β催化剂。The fourth aspect of this application provides a denitrification method that uses selective catalytic reduction to treat exhaust gas, using CH 4 as the reducing agent, and the aforementioned In/H-β catalyst as the catalyst.

本申请的第五方面,提供一种净化处理装置,该净化处理装置包括SCR反应器,SCR反应器内装设有前述的In/H-β催化剂。A fifth aspect of the present application provides a purification treatment device. The purification treatment device includes an SCR reactor, and the SCR reactor is equipped with the aforementioned In/H-β catalyst.

本申请的附加方面和优点将在下面的描述中部分给出,部分将从下面的描述中变得明显,或通过本申请的实践了解到。Additional aspects and advantages of the application will be set forth in part in the description which follows, and in part will be obvious from the description, or may be learned by practice of the application.

附图说明Description of the drawings

图1是本申请的脱硝活性对比试验的结果。其中,(a)是不同氨基酸介导制备得到的分子筛催化剂的氮氧化物去除率随温度的变化情况,(b)是不同氨基酸介导制备得到的分子筛催化剂的甲烷转化率随温度的变化情况,(c)是不同氨基酸介导制备得到的分子筛催化剂的甲烷选择性随温度的变化情况,(d)是In/H-β-P分子筛催化剂在多次TPSR循环中氮氧化物去除率的变化情况。Figure 1 is the result of the denitrification activity comparative test of the present application. Among them, (a) is the change of nitrogen oxide removal rate with temperature of molecular sieve catalysts prepared by different amino acids, (b) is the change of methane conversion rate with temperature of molecular sieve catalysts prepared by different amino acids, (c) is the change of methane selectivity with temperature of molecular sieve catalysts prepared by different amino acids, (d) is the change of nitrogen oxide removal rate of In/H-β-P molecular sieve catalyst in multiple TPSR cycles. .

图2是本申请的In/H-β-P、In/H-β-H、In/H-β-R、In/H-β-S和In/H-β-B分子筛催化剂的X射线衍射(XRD)图谱结果。Figure 2 is the X-ray of the In/H-β-P, In/H-β-H, In/H-β-R, In/H-β-S and In/H-β-B molecular sieve catalysts of the present application. Diffraction (XRD) pattern results.

图3是本申请的In/H-β-P和In/H-β-B分子筛催化剂的电子顺磁共振(EPR)光谱图。Figure 3 is an electron paramagnetic resonance (EPR) spectrum of the In/H-β-P and In/H-β-B molecular sieve catalysts of the present application.

图4是本申请的In/H-β-P样品的电镜以及结合能量色散X射线(EDX)图谱分析的成像结果。其中,a是扫描电镜的结果,图中标尺为1μm;b~f是电镜结合EDX图谱分析的结果,图中标尺为100nm,c~f分别反映Al、Si、O、In的元素分布。Figure 4 is an electron microscope and imaging result combined with energy dispersive X-ray (EDX) spectrum analysis of the In/H-β-P sample of the present application. Among them, a is the result of scanning electron microscopy, and the scale bar in the figure is 1 μm; b~f is the result of electron microscopy combined with EDX spectrum analysis, the scale bar in the figure is 100 nm, and c~f reflect the element distribution of Al, Si, O, and In respectively.

图5是本申请的In/H-β-P样品的透射电子显微镜(TEM)和高分辨率透射电子显微镜(HRTEM)的成像结果。其中,a中标尺为100nm,b的标尺为50nm,b中左下角为标尺10nm的晶格条纹。Figure 5 is the imaging results of transmission electron microscopy (TEM) and high-resolution transmission electron microscopy (HRTEM) of the In/H-β-P sample of the present application. Among them, the scale in a is 100nm, the scale in b is 50nm, and the lower left corner of b is the lattice stripe with a scale of 10nm.

图6是本申请的In/H-β-P样品的魔角旋转固态核磁(MAS NMR)检测结果。其中,a为29Si的结果,b为27Al的结果。Figure 6 is the magic angle rotation solid-state nuclear magnetic (MAS NMR) detection results of the In/H-β-P sample of the present application. Among them, a is the result of 29 Si, and b is the result of 27 Al.

图7是本申请的In/H-β-P、In/H-β-H、In/H-β-R和In/H-β-S分子筛催化剂的XPS测量光谱。其中,a为In 3d5/2光谱结果,b为O1s光谱结果。Figure 7 is the XPS measurement spectrum of the In/H-β-P, In/H-β-H, In/H-β-R and In/H-β-S molecular sieve catalysts of the present application. Among them, a is the In 3d 5/2 spectrum result, and b is the O1s spectrum result.

图8是本申请的In/H-β-P、In/H-β-H、In/H-β-R和In/H-β-S分子筛催化剂在氢程序升温还原(H2-TPR)下In的还原性结果。Figure 8 shows the hydrogen temperature programmed reduction (H 2 -TPR) of the In/H-β-P, In/H-β-H, In/H-β-R and In/H-β-S molecular sieve catalysts of the present application. Below are the reducibility results of In.

图9是本申请的In/H-β-P、In/H-β-H、In/H-β-R和In/H-β-S分子筛催化剂的NH3-TPD曲线。Figure 9 is the NH 3 -TPD curve of the In/H-β-P, In/H-β-H, In/H-β-R and In/H-β-S molecular sieve catalysts of the present application.

图10是本申请的In/H-β-P、In/H-β-H、In/H-β-R和In/H-β-S分子筛催化剂的吸附吡啶的红外光谱图(Py-IR)。Figure 10 is the infrared spectrum (Py-IR) of the adsorbed pyridine of the In/H-β-P, In/H-β-H, In/H-β-R and In/H-β-S molecular sieve catalysts of the present application. ).

具体实施方式Detailed ways

以下将结合实施例对本申请的构思及产生的技术效果进行清楚、完整地描述,以充分地理解本申请的目的、特征和效果。显然,所描述的实施例只是本申请的一部分实施例,而不是全部实施例,基于本申请的实施例,本领域的技术人员在不付出创造性劳动的前提下所获得的其他实施例,均属于本申请保护的范围。The concept of the present application and the technical effects produced will be clearly and completely described below in conjunction with the embodiments to fully understand the purpose, features and effects of the present application. Obviously, the described embodiments are only some of the embodiments of the present application, not all of the embodiments. Based on the embodiments of the present application, other embodiments obtained by those skilled in the art without exerting creative efforts are all The scope of protection of this application.

下面详细描述本申请的实施例,描述的实施例是示例性的,仅用于解释本申请,而不能理解为对本申请的限制。The embodiments of the present application are described in detail below. The described embodiments are exemplary and are only used to explain the present application and cannot be understood as limiting the present application.

在本申请的描述中,若干的含义是一个以上,多个的含义是两个以上,大于、小于、超过等理解为不包括本数,以上、以下、以内等理解为包括本数。如果有描述到第一、第二只是用于区分技术特征为目的,而不能理解为指示或暗示相对重要性或者隐含指明所指示的技术特征的数量或者隐含指明所指示的技术特征的先后关系。In the description of this application, several means one or more, plural means two or more, greater than, less than, exceeding, etc. are understood to exclude the original number, and above, below, within, etc. are understood to include the original number. If there is a description of first and second, it is only for the purpose of distinguishing technical features, and cannot be understood as indicating or implying the relative importance or implicitly indicating the number of indicated technical features or implicitly indicating the order of indicated technical features. relation.

本申请的描述中,参考术语“一个实施例”、“一些实施例”、“示意性实施例”、“示例”、“具体示例”、或“一些示例”等的描述意指结合该实施例或示例描述的具体特征、结构、材料或者特点包含于本申请的至少一个实施例或示例中。在本说明书中,对上述术语的示意性表述不一定指的是相同的实施例或示例。而且,描述的具体特征、结构、材料或者特点可以在任何的一个或多个实施例或示例中以合适的方式结合。In the description of this application, reference to the description of the terms "one embodiment," "some embodiments," "illustrative embodiments," "examples," "specific examples," or "some examples" is intended to be in conjunction with the description of the embodiment. or examples describe specific features, structures, materials, or characteristics that are included in at least one embodiment or example of the present application. In this specification, schematic representations of the above terms do not necessarily refer to the same embodiment or example. Furthermore, the specific features, structures, materials or characteristics described may be combined in any suitable manner in any one or more embodiments or examples.

实施例1Example 1

本实施例提供一种In/H-β催化剂,其制备方法如下:This embodiment provides an In/H-β catalyst, and its preparation method is as follows:

步骤1:将0.16g NaAlO2和0.05g NaOH溶解在12.5g四乙基氢氧化铵(TEAOH,25%)和2.6mL去离子水中,然后超声波条件下添加脯氨酸(P)以搅拌均匀,得到混合物。再将2g气相二氧化硅溶解在混合物中摇匀,得到反应凝胶。随后,将所得反应凝胶在磁力搅拌器中室温老化4h,使得反应凝胶中的组成以摩尔比计为0.3脯氨酸:1.0SiO2:0.023Al2O3:0.048Na2O:0.636TEAOH:20H2O。Step 1: Dissolve 0.16g NaAlO 2 and 0.05g NaOH in 12.5g tetraethylammonium hydroxide (TEAOH, 25%) and 2.6mL deionized water, then add proline (P) under ultrasonic conditions to stir evenly, A mixture is obtained. Then dissolve 2g of fumed silica in the mixture and shake well to obtain a reaction gel. Subsequently, the obtained reaction gel was aged for 4 h at room temperature in a magnetic stirrer, so that the composition in the reaction gel was 0.3 proline: 1.0 SiO 2 : 0.023 Al 2 O 3 : 0.048 Na 2 O: 0.636 TEAOH in terms of molar ratio. :20H 2 O.

步骤2:老化后的反应凝胶在均相反应器中在140℃温度条件下以10rpm的恒定速率旋转晶化48h。冷却至室温后,滤出分散液,去离子水冲洗至pH=7,然后在80℃下干燥12小时。最后,在500℃条件下空气气氛中对粉末进行3小时的焙烧,除去模板剂,得到Na-β分子筛。Step 2: The aged reaction gel is rotated and crystallized in a homogeneous reactor at a temperature of 140°C at a constant speed of 10 rpm for 48 hours. After cooling to room temperature, the dispersion was filtered, rinsed with deionized water to pH=7, and then dried at 80°C for 12 hours. Finally, the powder is calcined in an air atmosphere at 500°C for 3 hours to remove the template agent and obtain Na-β molecular sieve.

步骤3:将Na-β分子筛与1M(NH4)2SO4溶液按照1:20的固液质量比在85℃下进行4h的离子交换,然后过滤分离出固体,用蒸馏水洗涤,并在110℃下干燥。该离子交换程序重复两次,以确保完全阳离子交换。随后500℃条件下空气气氛中进行3小时的焙烧,得到H-β分子筛。Step 3: Perform ion exchange between Na-β molecular sieve and 1M (NH 4 ) 2 SO 4 solution at a solid-liquid mass ratio of 1:20 at 85°C for 4 hours, then filter to separate the solid, wash with distilled water, and incubate at 110 Dry at ℃. This ion exchange procedure was repeated twice to ensure complete cation exchange. Subsequently, it was calcined in an air atmosphere at 500°C for 3 hours to obtain H-β molecular sieve.

步骤4:将3g H-β分子筛溶解于100ml 0.033M的硝酸铟溶液中,并在85℃下进行8h的离子交换,然后过滤分离出固体,用蒸馏水洗涤,直到pH=7,并在80℃下干燥12小时。随后500℃条件下空气气氛中进行3小时的焙烧,得到In/H-β分子筛。Step 4: Dissolve 3g H-β molecular sieve in 100ml 0.033M indium nitrate solution, and perform ion exchange at 85°C for 8h, then filter to separate the solid, wash with distilled water until pH=7, and incubate at 80°C Dry for 12 hours. Subsequently, it was calcined in an air atmosphere at 500°C for 3 hours to obtain In/H-β molecular sieve.

对比例1~7,提供一种In/H-β分子筛,其制备方法与实施例1的区别在于,采用不同的氨基酸,具体分别为丙氨酸(A)、谷氨酸(E)、组氨酸(H)、丝氨酸(S)、苏氨酸(T)、精氨酸(R)和天冬氨酸(D)。为了将实施例1与对比例1~7区分,最终得到的分子筛产品在其后加上对应的氨基酸缩写X,记为In/H-β-X,如实施例1记为In/H-β-P,对比例1~7的产品分别记为In/H-β-A、In/H-β-E、In/H-β-H、In/H-β-S、In/H-β-T、In/H-β-R和In/H-β-D。Comparative Examples 1 to 7 provide an In/H-β molecular sieve. The difference between its preparation method and Example 1 is that different amino acids are used, specifically alanine (A), glutamic acid (E), Acid (H), serine (S), threonine (T), arginine (R) and aspartic acid (D). In order to distinguish Example 1 from Comparative Examples 1 to 7, the finally obtained molecular sieve product is followed by the corresponding amino acid abbreviation -P, the products of Comparative Examples 1 to 7 are respectively recorded as In/H-β-A, In/H-β-E, In/H-β-H, In/H-β-S, In/H-β -T, In/H-β-R and In/H-β-D.

对比例8,提供一种In/H-β分子筛,其制备方法与实施例1的区别在于,步骤1中不添加氨基酸。另外,由于不含氨基酸的影响,步骤2中的晶化时间延长为6天。该分子筛记为In/H-β-B。Comparative Example 8 provides an In/H-β molecular sieve. The difference between its preparation method and Example 1 is that no amino acid is added in step 1. In addition, due to the absence of the influence of amino acids, the crystallization time in step 2 is extended to 6 days. This molecular sieve is designated as In/H-β-B.

CH4-SCR性能对比试验CH 4 -SCR performance comparison test

使用连续流固定床反应器对In/H-β-X催化剂的NOx选择性催化还原进行了评估,具体过程如下:The In/H-β-X catalyst was evaluated for selective catalytic reduction of NOx using a continuous flow fixed-bed reactor. The specific process is as follows:

(1)将实施例1以及对比例1~8制得的分子筛催化剂在20MPa下制成颗粒,然后研磨,筛选出粒径为40-60目(0.250至0.425mm)的样品进行下一步反应。(1) Make the molecular sieve catalysts prepared in Example 1 and Comparative Examples 1 to 8 into particles at 20 MPa, then grind them, and screen out samples with a particle size of 40-60 mesh (0.250 to 0.425 mm) for the next reaction.

(2)称取100mg催化剂样品装入固定床连续流反应器中心。原料气含有400ppm NO、400ppm CH4、10vol.%O2、100ppm SO2、5vol.%H2O,其余为Ar作为平衡气体。原料气流速为100mL/min,空速(GHSV)23600h-1。反应器温度在100℃和650℃之间以4℃/min的温度梯度升高。(2) Weigh 100 mg of catalyst sample and put it into the center of the fixed-bed continuous flow reactor. The raw material gas contains 400 ppm NO, 400 ppm CH 4 , 10 vol.% O 2 , 100 ppm SO 2 , 5 vol. % H 2 O, and the rest is Ar as a balance gas. The raw gas flow rate is 100mL/min, and the space velocity (GHSV) is 23600h -1 . The reactor temperature was increased with a temperature gradient of 4°C/min between 100°C and 650°C.

使用程序升温表面反应(TPSR)技术监测催化剂活性。通过氮氧化物分析仪(ThermoScientific,42i)连续检测NO浓度。使用在线气相色谱仪(GC-2014C,日本岛津)测量CH4浓度,该气相色谱仪配备Porapak-Q柱和火焰离子化检测器(FID)。使用配备5A分子筛的安捷伦7890B GC分析SCR反应期间形成的N2O含量。Catalyst activity was monitored using temperature programmed surface reaction (TPSR) technology. NO concentration was measured continuously by a nitrogen oxide analyzer (ThermoScientific, 42i). CH concentration was measured using an online gas chromatograph (GC-2014C, Shimadzu, Japan) equipped with a Porapak-Q column and a flame ionization detector (FID). The N 2 O content formed during the SCR reaction was analyzed using an Agilent 7890B GC equipped with 5A molecular sieves.

在CH4-SCR反应过程中,理想状态下的反应式为:CH4+2NO+O2=CO2+N2+2H2O,氧气存在下CH4还原NOx生成氮气、水和二氧化碳。采用氮氧化物去除率(η)、甲烷转化率(γ)、甲烷选择性(α)、氮气选择性(SN2)四种指标来评价催化剂的脱硝活性。In the CH 4 -SCR reaction process, the ideal reaction formula is: CH 4 +2NO+O 2 =CO 2 +N 2 +2H 2 O. In the presence of oxygen, CH 4 reduces NO x to generate nitrogen, water and carbon dioxide. Four indicators are used to evaluate the denitrification activity of the catalyst: nitrogen oxide removal rate (η), methane conversion rate (γ), methane selectivity (α), and nitrogen selectivity (S N2 ).

式中,c(NOx)in为反应前NOx的初始浓度(ppm);In the formula, c(NO x ) in is the initial concentration of NO x before reaction (ppm);

c(NOx)out为反应后NOx的浓度(ppm);c(NO x ) out is the concentration of NO x after the reaction (ppm);

c(CH4)in为反应前CH4的初始浓度(ppm);c(CH 4 ) in is the initial concentration of CH 4 before reaction (ppm);

c(CH4)out为反应后CH4的浓度(ppm);c(CH 4 ) out is the concentration of CH 4 after the reaction (ppm);

c(N2O)为形成的N2O浓度(ppm)。c(N 2 O) is the concentration of N 2 O formed (ppm).

实施例1以及对比例1~8的脱硝活性的检测结果如图1所示,其中,a表示氮氧化物去除率结果。从a中可以看出,由不同氨基酸介导制成的In/H-β分子筛对氮氧化物的去除率也有明显区别,当使用脯氨酸介导的In/H-β-P时,在SO2和H2O干扰的情况下,氮氧化物去除率最高,可以达到40%,而对比例1~7的检测结果均不足30%。对比例8未采用氨基酸参与反应,其同等条件下氮氧化物去除率最高仅有10%。另外可以看到,In/H-β-D和In/H-β-T在600℃以下时,氮氧化物去除率几乎为0,即使在650℃,氮氧化物去除率仍然仅有3%不到。未添加氨基酸参与制备的In/H-β-B虽然在600℃以下时,氮氧化物去除率与前两者相似,但在650℃时氮氧化物去除率要明显比前两者更高。The detection results of the denitration activity of Example 1 and Comparative Examples 1 to 8 are shown in Figure 1, where a represents the nitrogen oxide removal rate result. It can be seen from a that the nitrogen oxide removal rates of In/H-β molecular sieves made of different amino acids are also significantly different. When using proline-mediated In/H-β-P, Under the interference of SO 2 and H 2 O, the nitrogen oxide removal rate is the highest, which can reach 40%, while the detection results of Comparative Examples 1 to 7 are all less than 30%. Comparative Example 8 did not use amino acids to participate in the reaction, and its nitrogen oxide removal rate was only 10% at the highest under the same conditions. In addition, it can be seen that the nitrogen oxide removal rate of In/H-β-D and In/H-β-T is almost 0 below 600°C. Even at 650°C, the nitrogen oxide removal rate is still only 3%. Less than. Although the nitrogen oxide removal rate of In/H-β-B prepared without adding amino acids is similar to the former two below 600°C, the nitrogen oxide removal rate at 650°C is significantly higher than the first two.

将氮氧化物去除率在20%以上的分子筛按照氮氧化物去除率从高到低排序为In/H-β-P(40%)>In/H-β-A(29%)>In/H-β-H(28.7%)>In/H-β-R(25.9%)>In/H-β-S(24.3%)>In/H-β-E(20.4%)。其中,由于In/H-β-A在低温条件下的氮氧化物去除率较低,因而不对其进行进一步表征,而仅对In/H-β-P、In/H-β-H、In/H-β-R、In/H-β-S进行进一步研究。Molecular sieves with a nitrogen oxide removal rate of more than 20% are sorted from high to low according to the nitrogen oxide removal rate as In/H-β-P (40%)>In/H-β-A (29%)>In/ H-β-H (28.7%)>In/H-β-R (25.9%)>In/H-β-S (24.3%)>In/H-β-E (20.4%). Among them, due to the low nitrogen oxide removal rate of In/H-β-A under low temperature conditions, it will not be further characterized, but only In/H-β-P, In/H-β-H, In /H-β-R, In/H-β-S for further study.

从图1的b中可以看出,随着温度的升高,四种分子筛都表现出较高的CH4转化率,四种催化剂之间没有明显差异,表明甲烷是关键还原剂,在所有CH4-SCR反应中消耗量大致相同。从图1的c中可以看出,四种分子筛的CH4选择性均为先升高再降低的趋势,在500℃左右具有最佳甲烷选择性。甲烷选择性与催化性能正相关,尤其是在低温区,在500℃时In/H-β-P的甲烷选择性最高,达到100%。因此,在最佳反应温度下,In/H-β-P可以实现CH4和NOx在CH4-SCR中理想的化学计量反应。当温度继续升高时,由于甲烷副反应的竞争,CH4选择性降低。As can be seen from Figure 1, b, as the temperature increases, all four molecular sieves show higher CH4 conversion rates, with no obvious difference between the four catalysts, indicating that methane is the key reducing agent, and in all CH 4 -The consumption in the SCR reaction is approximately the same. It can be seen from c in Figure 1 that the CH 4 selectivity of the four molecular sieves first increases and then decreases, with the best methane selectivity around 500°C. Methane selectivity is positively related to catalytic performance, especially in the low temperature region. The methane selectivity of In/H-β-P is the highest at 500°C, reaching 100%. Therefore, at the optimal reaction temperature, In/H-β-P can achieve the ideal stoichiometric reaction of CH4 and NOx in CH4 -SCR. When the temperature continues to increase, the CH selectivity decreases due to competition from methane side reactions.

此外,In/H-β-P催化剂在SO2和H2O干扰条件下,在重复试验中仍然表现出优异的耐久性,结果如图1的d所示,从上到下分别是第一次循环(1st)、第二次循环(2nd)、第三次(3rd)循环过程中的氮氧化物去除率的结果。从图中可以看出,即使在SO2和H2O干扰的情况下,经历了三次高达650℃的温度循环后,氮氧化物去除率几乎保持几乎相同,尤其是在高温区域,三次循环后,在650℃下仍然有高达37.9%的氮氧化物去除率。In addition, the In/H-β-P catalyst still showed excellent durability in repeated tests under the interference conditions of SO 2 and H 2 O. The results are shown in d of Figure 1, from top to bottom, respectively. The results of the nitrogen oxide removal rate during the first cycle (1st), the second cycle (2nd), and the third cycle (3rd). It can be seen from the figure that even under the interference of SO 2 and H 2 O, after experiencing three temperature cycles up to 650°C, the nitrogen oxide removal rate remains almost the same, especially in the high temperature area, after three cycles , there is still a nitrogen oxide removal rate of up to 37.9% at 650°C.

组成与结构表征Composition and structural characterization

ICP法测量In/H-β-P、In/H-β-H、In/H-β-R、In/H-β-S和In/H-β-B的铟含量和Si/Al比率,结果如表1所示。ICP method to measure the indium content and Si/Al ratio of In/H-β-P, In/H-β-H, In/H-β-R, In/H-β-S and In/H-β-B , the results are shown in Table 1.

表1.分子筛中的元素含量比较Table 1. Comparison of element content in molecular sieves

从表中可以看出,催化剂的Si/Al比大致在25左右,这也接近于起始的反应凝胶的比例。之前的研究结果表明,H-β分子筛利用0.033M的铟溶液进行离子交换制备得到的约7wt%的铟含量的In/H-β分子筛具有最佳的NO去除效率。而上述方法中制备得到的分子筛中的铟含量在5.7-7.1wt%范围内,铟含量从最低到最高为In/H-β-S<In/H-β-P<In/H-β-H<In/H-β-R<In/H-β-B。这一趋势与NO在CH4-SCR中的催化活性顺序不一致,表明铟负载量可能不是导致高脱硝效率的关键因素。另一方面,In/H-β-P的最佳脱硝催化剂具有最高的In/Al比0.8,表明其具有最高的离子交换度。As can be seen from the table, the Si/Al ratio of the catalyst is roughly around 25, which is also close to the ratio of the initial reaction gel. Previous research results have shown that the In/H-β molecular sieve with an indium content of approximately 7wt%, prepared by ion exchange with a 0.033M indium solution, has the best NO removal efficiency. The indium content in the molecular sieve prepared by the above method is in the range of 5.7-7.1wt%, and the indium content from the lowest to the highest is In/H-β-S<In/H-β-P<In/H-β- H<In/H-β-R<In/H-β-B. This trend is inconsistent with the order of catalytic activity of NO in CH4 -SCR, indicating that the indium loading may not be the key factor leading to high denitrification efficiency. On the other hand, the best denitration catalyst of In/H-β-P has the highest In/Al ratio of 0.8, indicating that it has the highest degree of ion exchange.

图2显示了In/H-β-P、In/H-β-H、In/H-β-R、In/H-β-S和In/H-β-B分子筛催化剂的X射线衍射(XRD)图谱。在In/H-β-P、In/H-β-H、In/H-β-R和In/H-β-S中可以观察到与H-β分子筛对应的7.8°、13.5°、21.5°、22.5°、25.2°、27.1°、29.7°、33.4°和43.7°的特征反射。因此,在氨基酸的作用下,无杂质的纯结晶β相可以在2天内完全结晶。同时,其中未检测到In2O3的峰,这表明铟已成功地以骨架外阳离子的形式交换,且处于高度分散状态,通过X射线衍射检测到的氧化铟量可忽略不计。而In/H-β-B样品仅在32°左右的位置处显示出宽峰,表明即使将结晶时间延长3倍到6天,其中也仍然存在非晶相。Figure 2 shows the X-ray diffraction of In/H-β-P, In/H-β-H, In/H-β-R, In/H-β-S and In/H-β-B molecular sieve catalysts ( XRD) pattern. In In/H-β-P, In/H-β-H, In/H-β-R and In/H-β-S, 7.8°, 13.5°, and 21.5 corresponding to H-β molecular sieves can be observed. °, 22.5°, 25.2°, 27.1°, 29.7°, 33.4° and 43.7° characteristic reflections. Therefore, under the action of amino acids, the pure crystalline β phase without impurities can be completely crystallized within 2 days. At the same time, no peak of In 2 O 3 was detected, which indicates that indium has been successfully exchanged in the form of extra-framework cations and is in a highly dispersed state, and the amount of indium oxide detected by X-ray diffraction is negligible. The In/H-β-B sample only shows a broad peak at about 32°, indicating that even if the crystallization time is extended by 3 times to 6 days, the amorphous phase still exists in it.

根据上述结果推测,氨基酸的添加促进了β分子筛的结晶,进一步验证试验如下:将5,5-二甲基吡咯啉-N-氧化物(DMPO)添加到初始合成的反应凝胶中。比较由含有脯氨酸合成Na-β-P凝胶和不含氨基酸合成的Na-β-B凝胶的原位EPR光谱,结果如图3。从图中可以看出两者存在明显的差异。由于DMPO-·OH的共振跃迁,Na-β-P以1:2:2:1的比例呈现四重模式,分裂为1.5mT,而Na-β-B则完全没有Na-β-P的这种模式。因此,氨基酸的促结晶作用可能是由诱导自由基引起的。Based on the above results, it is speculated that the addition of amino acids promotes the crystallization of β molecular sieves. Further verification tests are as follows: 5,5-dimethylpyrroline-N-oxide (DMPO) is added to the initially synthesized reaction gel. Comparing the in-situ EPR spectra of Na-β-P gel synthesized with proline and Na-β-B gel synthesized without amino acids, the results are shown in Figure 3. It can be seen from the figure that there are obvious differences between the two. Due to the resonance transition of DMPO-·OH, Na-β-P presents a quadruple mode in the ratio of 1:2:2:1, splitting into 1.5mT, while Na-β-B does not have this characteristic of Na-β-P at all. a pattern. Therefore, the pro-crystallization effect of amino acids may be caused by the induction of free radicals.

对分子筛的结构性质进行分析,结果如表2所示。其中,SBET为BET表面积,由氮气吸附法在相对气压范围在0.05~0.3时测得;Vtotal为总孔体积,由P/P0=0.98时吸附的氮气量计算得到;Vmeso为中孔体积,由t图法(t-plot)计算得到;dmeso为中孔直径,由BJH法计算得到。The structural properties of molecular sieves were analyzed, and the results are shown in Table 2. Among them, S BET is the BET surface area, measured by the nitrogen adsorption method when the relative pressure range is 0.05 to 0.3; V total is the total pore volume, calculated from the amount of nitrogen adsorbed when P/P 0 = 0.98; V meso is the medium The pore volume is calculated by the t-plot method; d meso is the mesopore diameter, which is calculated by the BJH method.

表2.分子筛结构分析结果Table 2. Molecular sieve structure analysis results

从表中可以看出,In/H-β-P显示最高中孔体积为0.27cm3/g,最高总孔体积为0.42cm3/g;其次是In/H-β-S和In/H-β-R。In/H-β-P具有最高中孔体积和总孔体积的可能原因是其与分子筛合成具有更好的相容性,以及脯氨酸分子的独特环状侧链的特殊稳定性。但是可以看到,分子筛的介孔大小与其氮氧化物去除率以及甲烷选择性等并不完全一致。As can be seen from the table, In/H-β-P shows the highest mesopore volume of 0.27cm 3 /g and the highest total pore volume of 0.42cm 3 /g; followed by In/H-β-S and In/H -β-R. The possible reasons why In/H-β-P has the highest mesopore volume and total pore volume are its better compatibility with molecular sieve synthesis and the special stability of the unique cyclic side chain of the proline molecule. However, it can be seen that the mesopore size of molecular sieves is not completely consistent with its nitrogen oxide removal rate and methane selectivity.

对In/H-β-P样品使用扫描电子显微镜(SEM)结合能量色散X射线(EDX)图谱分析纳米级形态和组成,结果如图4所示,其中,a是扫描电镜的结果,b~f是EDX图谱的定量分析结果,从图中可以清楚地观察到平均晶粒尺寸为~150nm的均匀纳米颗粒,Al、Si和O元素在分子筛中均匀分布,而In同样在整个分子筛中较为均匀地分布,但在表面有轻微的聚集。根据EDX分析结果,铟的重量浓度大约为6%,与ICP分析结果一致,证实了铟在晶体表面和内部的分布均匀。Scanning electron microscopy (SEM) combined with energy dispersive X-ray (EDX) spectrum was used to analyze the nanoscale morphology and composition of the In/H-β-P sample. The results are shown in Figure 4, where a is the result of the scanning electron microscope, and b~ f is the quantitative analysis result of the EDX spectrum. It can be clearly observed from the figure that uniform nanoparticles with an average grain size of ~150nm are observed. Al, Si and O elements are evenly distributed in the molecular sieve, while In is also relatively uniform throughout the molecular sieve. Geographically distributed, but slightly aggregated on the surface. According to the EDX analysis results, the weight concentration of indium is approximately 6%, which is consistent with the ICP analysis results, confirming that indium is evenly distributed on the surface and interior of the crystal.

对In/H-β-P样品进行透射电子显微镜(TEM)成像,结果如图5的a所示,表明In/H-β-P分子筛的镶嵌结构,其中有大量尺寸为10-20nm的微晶共生成中晶体,形成明显的具有明确边缘的纳米介孔。通过高分辨率TEM(HRTEM)进行进一步检查,结果如图5的b所示,表明颗粒是完全结晶的,通过遍布试样的大量晶格条纹可以证明(b左下插图)。这些介孔的存在使得反应物和产物易于运输,同时防止副反应。因此,脯氨酸的调节导致In/H-β-P显示出更多暴露的活性催化位点。这些活性催化位点可以增强水热稳定性和抗中毒性。Transmission electron microscopy (TEM) imaging was performed on the In/H-β-P sample. The results are shown in Figure 5a, indicating the mosaic structure of the In/H-β-P molecular sieve, in which there are a large number of microstructures with a size of 10-20 nm. The crystals co-generate medium crystals, forming obvious nanometer mesopores with clear edges. Further inspection was carried out by high-resolution TEM (HRTEM), and the results, shown in Figure 5, b, indicate that the particles are fully crystalline, as evidenced by the large number of lattice fringes spread across the specimen (b, lower left inset). The presence of these mesopores allows easy transportation of reactants and products while preventing side reactions. Therefore, the modulation of proline resulted in In/H-β-P showing more exposed active catalytic sites. These active catalytic sites can enhance hydrothermal stability and resistance to toxicity.

魔角旋转固态核磁(MAS NMR)检测In/H-β-P样品的配位结构,结果如图6所示,其中,a为29Si的结果,b是27Al的结果。从a中可以看出,29Si MAS NMR显示了-110.8ppm处的一个主峰和-102.6ppm处的一个肩峰,前者是H-β晶格中独特的硅四面体结构的特征,后者由于Si-O-Al(Si)键的水解,对应于Si-OH-Al(Si)。在-110.8ppm左右的峰宽可能是由于β框架中的不同Si位。而Si-OH-Al(Si)则通常被认为是In/H-β催化剂上酸中心的来源。从b中可以看出,27Al MAS NMR显示了54.8和57.6ppm处的两个主峰,分别对应于T1-T2和T3-T9骨架铝位的β沸石中的四面体配位。这些四面体配位的Al位点,电荷为3+,产生带负电荷的骨架,该骨架由可交换阳离子(如含In的阳离子)补偿。而接近0ppm的弱峰表明In/H-β-P中的八面体铝含量可忽略不计。Magic angle rotation solid-state nuclear magnetic resonance (MAS NMR) was used to detect the coordination structure of the In/H-β-P sample. The results are shown in Figure 6, where a is the result of 29 Si and b is the result of 27 Al. As can be seen from a, 29 Si MAS NMR shows a main peak at -110.8ppm and a shoulder peak at -102.6ppm. The former is a characteristic of the unique silicon tetrahedral structure in the H-β lattice, and the latter is due to Hydrolysis of the Si-O-Al(Si) bond, corresponding to Si-OH-Al(Si). The peak width around -110.8 ppm may be due to different Si sites in the β framework. Si-OH-Al(Si) is usually considered to be the source of acid sites on In/H-β catalysts. As can be seen from b, 27 Al MAS NMR shows two main peaks at 54.8 and 57.6 ppm, corresponding to the tetrahedral coordination in β zeolite at T1-T2 and T3-T9 framework aluminum positions, respectively. These tetrahedrally coordinated Al sites, with a charge of 3+, produce a negatively charged skeleton that is compensated by exchangeable cations such as In-containing cations. The weak peak close to 0 ppm indicates that the octahedral aluminum content in In/H-β-P is negligible.

化学状态与氧化还原实验Chemical states and redox experiments

In/H-β-P、In/H-β-H、In/H-β-R、In/H-β-S和In/H-β-B的光电子能谱(XPS)结果如图7所示,其中,a是In 3d5/2光谱的测量结果,从中可以看出,其中三种铟化学状态分别对应于约445eV的In2O3、约446eV的InO+和约447eV的In(OH)3-z z+。表3比较了这些铟状态的曲线拟合含量,表明四种催化剂中三种铟的比例几乎相同。交换态InO+和In(OH)3-z z+是铟的主要类型,而交换的InO+物种是CH4-SCR反应的活性位点。另一方面,In/H-β-X催化剂的结合能(BE)值在不同的催化剂中有所不同。对于In/H-β-P,三种类型铟的BE值均最高,表明铟与脯氨酸调制的β沸石框架的相互作用更强。Photoelectron spectroscopy (XPS) results of In/H-β-P, In/H-β-H, In/H-β-R, In/H-β-S and In/H-β-B are shown in Figure 7 is shown, where a is the measurement result of the In 3d 5/2 spectrum, from which it can be seen that the three chemical states of indium correspond to In 2 O 3 at about 445eV, InO + at about 446eV, and In(OH at about 447eV). ) 3-z z+ . Table 3 compares the curve-fit contents of these indium states, showing that the proportions of the three indium species in the four catalysts are nearly identical. The exchanged InO + and In(OH) 3-z z+ are the main types of indium, and the exchanged InO + species are the active sites of the CH4 - SCR reaction. On the other hand, the binding energy (BE) values of In/H-β-X catalysts vary among different catalysts. For In/H-β-P, the BE values of the three types of indium are the highest, indicating that indium has a stronger interaction with the proline-modulated beta zeolite framework.

b是O1s光谱的测量结果,从图中可以看出,在532.7eV和533.6eV处解卷积为两个主峰,对应于表面上不同形式的氧:Oβ的表面氧和Oγ的羟基内的氧。由于其高迁移率,Oβ可以参与氧化过程,该过程对NO的SCR起着关键作用。通过反褶积和曲线拟合,获得了样品中的Oβ/(Oβ+Oγ)比值,结果参考表3,在0.57-0.59之间的窄范围内,没有显著差异。因此,不同的氨基酸介导不会改变催化剂表面氧元素的化学价态。b is the measurement result of O1s spectrum. It can be seen from the figure that it is deconvoluted into two main peaks at 532.7eV and 533.6eV, corresponding to different forms of oxygen on the surface: surface oxygen of and hydroxyl group of of oxygen. Due to its high mobility, can participate in the oxidation process, which plays a key role in the SCR of NO. Through deconvolution and curve fitting, the O β /(O β + O γ ) ratio in the sample was obtained. The results are referred to Table 3. There is no significant difference in the narrow range between 0.57-0.59. Therefore, different amino acid mediations will not change the chemical valence state of oxygen elements on the catalyst surface.

表3.分子筛催化剂表面元素化学状态Table 3. Chemical state of surface elements of molecular sieve catalysts

氢气程序升温还原(H2-TPR)研究不同分子筛样品中In的还原性,结果如图8所示。从图中可以看出,所有样品在200℃和500℃之间均表现出广泛的还原信号,峰值集中在300-400℃,该结果表明不存在需要更高还原温度的大块In2O3,从侧面说明掺入的In3+处于高度分散状态。In/H-β-P的还原峰出现在以~365℃为中心的最高温度,说明其还原温度要求较高,这可能表明铟与沸石骨架的电子相互作用更强,从而延缓氧化铟的还原。Hydrogen temperature programmed reduction (H 2 -TPR) was used to study the reducing properties of In in different molecular sieve samples. The results are shown in Figure 8. As can be seen from the figure, all samples exhibit a broad reduction signal between 200°C and 500°C, with peaks concentrated at 300-400°C. This result indicates that there is no bulk In 2 O 3 that requires a higher reduction temperature. , indicating from the side that the incorporated In 3+ is in a highly dispersed state. The reduction peak of In/H-β-P appears at the highest temperature centered at ~365°C, indicating that its reduction temperature requirement is higher. This may indicate that the electronic interaction between indium and the zeolite framework is stronger, thereby delaying the reduction of indium oxide. .

表面酸度实验Surface acidity experiment

之前的结果表明,调节H-β分子筛催化剂中的Si/Al比率会改变金属氧化物/β催化剂中复合物中的酸中心数量。但在本方案中,所有H-β-X样品中Si/Al比率均保持在~25左右。XPS光谱和H2-TPR结果也证明它们的表面铟和氧物种相似。高结合能揭示的铟物种与In/H-β-P框架的更强相互作用表明,脯氨酸可能改善了沸石性质。因此,进一步对其表面酸度进行研究。Previous results have shown that adjusting the Si/Al ratio in H-β molecular sieve catalysts changes the number of acid sites in the composite in metal oxide/β catalysts. However, in this scheme, the Si/Al ratio remains around ∼25 in all H-β-X samples. XPS spectra and H 2 -TPR results also prove that their surface indium and oxygen species are similar. The stronger interaction of the indium species with the In/H-β-P framework revealed by the high binding energy suggests that proline may improve the zeolite properties. Therefore, its surface acidity was further investigated.

In/H-β-P、In/H-β-H、In/H-β-R和In/H-β-S催化剂的NH3-TPD曲线如图9所示。这些NH3-TPD曲线可分解为位于200℃以下的峰Ⅰ,对应弱酸位点;位于200-350℃之间的峰Ⅱ,对应中酸位点;位于350-650℃之间的峰Ⅲ,对应强酸位点。表4为NH3-TPD曲线的拟合结果,从中可以看出,In/H-β-P具有最高数量的酸位,尤其是强酸位。酸位数的顺序为In/H-β-P、In/H-β-H、In/H-β-R和In/H-β-S,与图1所反映的CH4-SCR性能密切相关,证实了酸位对脱硝催化的重要作用。The NH 3 -TPD curves of In/H-β-P, In/H-β-H, In/H-β-R and In/H-β-S catalysts are shown in Figure 9. These NH 3 -TPD curves can be decomposed into peak I located below 200°C, corresponding to weak acid sites; peak II located between 200-350°C, corresponding to medium acid sites; peak III located between 350-650°C, Corresponds to strong acid sites. Table 4 shows the fitting results of the NH 3 -TPD curve. It can be seen that In/H-β-P has the highest number of acid sites, especially strong acid sites. The order of acid number is In/H-β-P, In/H-β-H, In/H-β-R and In/H-β-S, which is closely related to the CH 4 -SCR performance reflected in Figure 1 Related, confirming the important role of acid sites in denitration catalysis.

表4.分子筛催化剂表面酸中心的数量和分布Table 4. Number and distribution of acid sites on the surface of molecular sieve catalysts

a:峰值对应温度(℃)。a: Peak corresponding temperature (°C).

b:峰面积(a.u.)。b: Peak area (a.u.).

c:计算方法:积分摩尔消光系数(IMEC)。c: Calculation method: Integrated molar extinction coefficient (IMEC).

吡啶(Py)相比于NH3具有更高的选择性和稳定性,可以通过FTIR光谱轻松区分sted和Lewis酸性位点。四种催化剂的吸附吡啶的红外光谱(Py-IR)如图10所示。1540cm-1和1450cm-1左右的谱带分别对应吡啶吸附在/>酸位上形成的吡啶离子(PyH+)和与Lewis酸位相互作用的吡啶。1490cm-1处的谱带则由PyH+和与Lewis酸位配位的吡啶共同作用形成。根据1540cm-1和1450cm-1处的谱带估计/>酸、Lewis酸和B/L的量,结果如表4所示。与NH3-TPD结果一致,/>酸的量和B/L比的顺序为In/H-β-P>In/H-β-H>In/H-β-R>In/H-β-S,与催化活性呈正相关。因此,在使用In/H-β催化剂的CH4-SCR中,强酸中心的数量和/>酸中心的密度起着至关重要的作用。另外结合表2的数据可以看出,氨基酸的介导作用是在不影响骨架硅铝比的情况下调整了分子筛的催化活性。Pyridine (Py) has higher selectivity and stability than NH3 and can be easily distinguished by FTIR spectroscopy sted and Lewis acidic sites. The infrared spectra (Py-IR) of adsorbed pyridine on the four catalysts are shown in Figure 10. The bands around 1540cm -1 and 1450cm -1 respectively correspond to the adsorption of pyridine on/> The pyridinium ion (PyH+) formed at the acid site and the pyridine interacting with the Lewis acid site. The band at 1490cm -1 is formed by the interaction of PyH+ and pyridine coordinated with Lewis acid. Estimated based on the spectral bands at 1540cm -1 and 1450cm -1 /> The amount of acid, Lewis acid and B/L, the results are shown in Table 4. Consistent with the NH 3 -TPD results,/> The order of acid amount and B/L ratio is In/H-β-P>In/H-β-H>In/H-β-R>In/H-β-S, which is positively correlated with catalytic activity. Therefore, in CH 4 -SCR using In/H-β catalyst, the number of strong acid sites and/> The density of the acid centers plays a crucial role. In addition, combined with the data in Table 2, it can be seen that the mediated effect of amino acids adjusts the catalytic activity of the molecular sieve without affecting the silicon-aluminum ratio of the framework.

结合NH3-TPD和Py-IR结果,In/H-β-P催化剂表现出最佳的CH4-SCR活性的原因是其具有更强的酸活性中心,因而有助于与氧化铟和羟基铟物种更强的相互作用。另外,比较了In/H-β-P和脯氨酸的FT-IR光谱,在In/H-β-P中未发现脯氨酸的特征FT-IR峰,因此,脯氨酸仅在合成阶段与β分子筛骨架相互作用,随后的洗涤和焙烧步骤已经将其完全去除。即,脯氨酸的加入仅仅是调节生成的催化剂的酸度,而并不会加入到最终形成的催化剂中。Combining the NH 3 -TPD and Py-IR results, the reason why the In/H-β-P catalyst shows the best CH 4 -SCR activity is that it has stronger The acid active center thus facilitates stronger interactions with indium oxide and indium hydroxy species. In addition, the FT-IR spectra of In/H-β-P and proline were compared. The characteristic FT-IR peak of proline was not found in In/H-β-P. Therefore, proline is only synthesized in In/H-β-P. stage interacts with the beta molecular sieve framework, which has been completely removed by subsequent washing and roasting steps. That is, the addition of proline only adjusts the acidity of the generated catalyst, but will not be added to the final catalyst.

实施例2Example 2

本实施例提供一种In/H-β催化剂的制备方法,与实施例1的区别在于,晶化温度为220℃,晶化时间为48小时。该方法制备得到的In/H-β催化剂采用上述相同的检测条件发现在SO2和H2O干扰下,同样维持了较高的氮氧化物去除率以及甲烷选择性。This embodiment provides a method for preparing an In/H-β catalyst. The difference from Example 1 is that the crystallization temperature is 220°C and the crystallization time is 48 hours. The In/H-β catalyst prepared by this method was found to maintain a high nitrogen oxide removal rate and methane selectivity under the interference of SO 2 and H 2 O using the same detection conditions mentioned above.

实施例3~6Examples 3 to 6

实施例3~6分别提供一种In/H-β催化剂的制备方法,与实施例1的区别在于,调节脯氨酸的量使得老化后反应凝胶中脯氨酸与二氧化硅的摩尔比值为0.1、0.2、0.4、0.5。参考上述的方法进行检测,发现在SO2和H2O干扰下,相比于相同条件下使用其它氨基酸或不使用氨基酸的制备方法,实施例3~6制得的分子筛催化剂同样维持了较高的氮氧化物去除率以及甲烷选择性。Examples 3 to 6 respectively provide a method for preparing an In/H-β catalyst. The difference from Example 1 is that the amount of proline is adjusted so that the molar ratio of proline to silica in the reaction gel after aging is are 0.1, 0.2, 0.4, 0.5. Referring to the above method for testing, it was found that under the interference of SO 2 and H 2 O, compared with the preparation method using other amino acids or not using amino acids under the same conditions, the molecular sieve catalysts prepared in Examples 3 to 6 also maintained a higher nitrogen oxide removal rate and methane selectivity.

实施例7~9Examples 7 to 9

实施例7~9分别提供一种In/H-β催化剂的制备方法,与实施例1的区别在于,调节硝酸铟溶液的浓度分别为0.01M、0.06M和0.1M。这些方法制备得到的In/H-β催化剂采用上述相同的检测条件发现在SO2和H2O干扰下,同样维持了较高的氮氧化物去除率以及甲烷选择性。Examples 7 to 9 respectively provide a method for preparing an In/H-β catalyst. The difference from Example 1 is that the concentrations of the indium nitrate solution are adjusted to 0.01M, 0.06M and 0.1M respectively. The In/H-β catalyst prepared by these methods was found to maintain a high nitrogen oxide removal rate and methane selectivity under the interference of SO 2 and H 2 O using the same detection conditions mentioned above.

实施例10Example 10

本实施例提供一种废气处理装置,该废气处理装置包括至少一个SCR反应器,该SCR反应器的一端连接有输入流系统,该输入流系统包括多个入口,分别用于向SCR反应器内通入甲烷和废气。在SCR反应器内还预置有实施例1~9中任一种方法制备得到的In/H-β催化剂。This embodiment provides an exhaust gas treatment device. The exhaust gas treatment device includes at least one SCR reactor. One end of the SCR reactor is connected to an input flow system. The input flow system includes a plurality of inlets, respectively for supplying water into the SCR reactor. Introduce methane and waste gas. The In/H-β catalyst prepared by any one of the methods in Examples 1 to 9 is also pre-installed in the SCR reactor.

上面结合实施例对本申请作了详细说明,但是本申请不限于上述实施例,在所属技术领域普通技术人员所具备的知识范围内,还可以在不脱离本申请宗旨的前提下作出各种变化。此外,在不冲突的情况下,本申请的实施例及实施例中的特征可以相互组合。The present application has been described in detail above with reference to the embodiments. However, the present application is not limited to the above-mentioned embodiments. Various changes can be made within the knowledge scope of those of ordinary skill in the art without departing from the purpose of the present application. In addition, the embodiments of the present application and the features in the embodiments may be combined with each other without conflict.

Claims (9)

1. In/H-β催化剂的制备方法,其特征在于,包括以下步骤:1. The preparation method of In/H-β catalyst is characterized by comprising the following steps: 步骤1:取包括氨基酸、硅源、铝源、M源、有机胺模板剂、水的原料混合反应,得到反应凝胶;Step 1: Mix and react raw materials including amino acids, silicon sources, aluminum sources, M sources, organic amine templates, and water to obtain a reaction gel; 步骤2:将所述反应凝胶晶化,冷却后洗涤、干燥、焙烧,得到M-β分子筛;Step 2: Crystallize the reaction gel, cool, wash, dry and roast to obtain M-β molecular sieve; 步骤3:将M-β分子筛与铵盐溶液混合反应,完成离子交换后洗涤、干燥、焙烧,得到H-β分子筛;Step 3: Mix and react M-β molecular sieve with ammonium salt solution, complete ion exchange, wash, dry and roast to obtain H-β molecular sieve; 步骤4:将H-β分子筛与铟盐溶液混合反应,完成离子交换后洗涤、干燥、焙烧,得到In/H-β分子筛;Step 4: Mix and react H-β molecular sieve with indium salt solution, complete ion exchange, wash, dry and roast to obtain In/H-β molecular sieve; 其中,M为碱金属、碱土金属中的至少一种,所述氨基酸为脯氨酸。Wherein, M is at least one of an alkali metal and an alkaline earth metal, and the amino acid is proline. 2.根据权利要求1所述的制备方法,其特征在于,在所述反应凝胶中,所述硅源以二氧化硅计,氨基酸/二氧化硅的摩尔比值为0.1~0.5。2. The preparation method according to claim 1, characterized in that, in the reaction gel, the silicon source has a molar ratio of amino acid/silica calculated as silica from 0.1 to 0.5. 3.根据权利要求2所述的制备方法,其特征在于,所述铝源、所述M源以氧化物计,所述有机胺模板剂以季铵离子计,二氧化硅/氧化铝的摩尔比值为5~200,氧化M/二氧化硅的摩尔比为0.01~0.4,季铵离子/二氧化硅的摩尔比值为0.1~0.8。3. The preparation method according to claim 2, characterized in that the aluminum source and the M source are calculated as oxides, the organic amine template agent is calculated as quaternary ammonium ions, and the mole of silicon dioxide/alumina The ratio is 5~200, the molar ratio of M oxide/silica is 0.01~0.4, and the molar ratio of quaternary ammonium ions/silica is 0.1~0.8. 4.根据权利要求1至3任一项所述的制备方法,其特征在于,步骤2~4中焙烧温度为400~600℃,焙烧时间为1~6h。4. The preparation method according to any one of claims 1 to 3, characterized in that in steps 2 to 4, the roasting temperature is 400-600°C, and the roasting time is 1-6 hours. 5.权利要求1至4任一项所述的制备方法制得的In/H-β催化剂。5. In/H-β catalyst prepared by the preparation method according to any one of claims 1 to 4. 6. 根据权利要求5所述的In/H-β催化剂,其特征在于,Brønsted酸位点的浓度为50 μmol/g以上。6. The In/H-β catalyst according to claim 5, characterized in that the concentration of Brønsted acid sites is above 50 μmol/g. 7.根据权利要求6所述的In/H-β催化剂,其特征在于,Brønsted酸位点/Lewis酸位点的浓度比值为0.55以上。7. The In/H-β catalyst according to claim 6, characterized in that the concentration ratio of Brønsted acid sites/Lewis acid sites is above 0.55. 8.脱硝方法,其特征在于,采用选择性催化还原法对废气进行处理,以CH4为还原剂,催化剂选用权利要求5至7中任一项所述的In/H-β催化剂。8. Denitrification method, characterized in that the exhaust gas is treated by selective catalytic reduction, CH4 is used as the reducing agent, and the In/H-β catalyst according to any one of claims 5 to 7 is selected as the catalyst. 9.净化处理装置,其特征在于,包括SCR反应器,所述SCR反应器内装设有权利要求5至7中任一项所述的In/H-β催化剂。9. Purification treatment device, characterized in that it includes an SCR reactor, and the SCR reactor is equipped with the In/H-β catalyst according to any one of claims 5 to 7.
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