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CN107126973A - A kind of in-situ synthetic method of catalyst of CuFe SAPO 34 and its application - Google Patents

A kind of in-situ synthetic method of catalyst of CuFe SAPO 34 and its application Download PDF

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CN107126973A
CN107126973A CN201710398412.9A CN201710398412A CN107126973A CN 107126973 A CN107126973 A CN 107126973A CN 201710398412 A CN201710398412 A CN 201710398412A CN 107126973 A CN107126973 A CN 107126973A
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谢利娟
阮文权
邓芸
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    • B01J29/85Silicoaluminophosphates [SAPO compounds]
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    • B01DSEPARATION
    • B01D53/00Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
    • B01D53/34Chemical or biological purification of waste gases
    • B01D53/92Chemical or biological purification of waste gases of engine exhaust gases
    • B01D53/94Chemical or biological purification of waste gases of engine exhaust gases by catalytic processes
    • B01D53/9404Removing only nitrogen compounds
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    • C01B37/06Aluminophosphates containing other elements, e.g. metals, boron
    • C01B37/08Silicoaluminophosphates [SAPO compounds], e.g. CoSAPO
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    • C01B39/00Compounds having molecular sieve and base-exchange properties, e.g. crystalline zeolites; Their preparation; After-treatment, e.g. ion-exchange or dealumination
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    • B01D2258/012Diesel engines and lean burn gasoline engines

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Abstract

本发明公开了一种CuFe‑SAPO‑34催化剂的原位合成方法及其应用,属于催化技术领域。本发明方法包括以下步骤:将拟薄水铝石加入去离子水中进行搅拌溶解,然后加入正磷酸和气相法二氧化硅,待混匀后加入铜盐和四乙烯五胺,充分搅拌后加入Fe盐和正丙胺;将搅拌完全的凝胶装入水热反应釜中晶化,晶化反应完成后冷却至室温,将固体结晶产物与母液分离,用去离子水洗涤至中性,干燥,然后在空气中焙烧,得到CuFe‑SAPO‑34小孔分子筛催化剂。本发明采用一步合成法制备CuFe‑SAPO‑34催化剂,经过优选Fe的负载量,显著提高了Cu‑SAPO‑34催化剂的催化性能及低温抗水性能。

The invention discloses an in-situ synthesis method and application of CuFe-SAPO-34 catalyst, belonging to the technical field of catalysis. The method of the present invention comprises the following steps: adding pseudo-boehmite into deionized water for stirring and dissolving, then adding orthophosphoric acid and fumed silicon dioxide, adding copper salt and tetraethylenepentamine after mixing, adding Fe after fully stirring salt and n-propylamine; put the fully stirred gel into a hydrothermal reaction kettle for crystallization, cool to room temperature after the crystallization reaction is completed, separate the solid crystalline product from the mother liquor, wash with deionized water until neutral, dry, and then Roasting in air to obtain CuFe-SAPO-34 small-pore molecular sieve catalyst. The present invention adopts a one-step synthesis method to prepare the CuFe-SAPO-34 catalyst, and the catalytic performance and the low-temperature water resistance performance of the Cu-SAPO-34 catalyst are significantly improved by optimizing the loading amount of Fe.

Description

一种CuFe-SAPO-34催化剂的原位合成方法及其应用A kind of in-situ synthesis method and application of CuFe-SAPO-34 catalyst

技术领域technical field

本发明涉及一种CuFe-SAPO-34催化剂的原位合成方法及其应用,属于催化技术领域。The invention relates to an in-situ synthesis method and application of a CuFe-SAPO-34 catalyst, belonging to the technical field of catalysis.

背景技术Background technique

NOx会导致雾霾、酸雨、光化学烟雾等大气污染问题,是目前重要的大气污染物,也是我国目前我国大气污染防治的重点对象。人们工业生产及生活活动带来的化石燃料燃烧是氮氧化物(NOx)主要来源。在人为源NOx排放中,以燃煤电厂烟气为代表的固定源和柴油车尾气为代表的移动源的NOx占据了大约60%的排放份额。随国家排放法规标准的提高,移动源NOx排放达标需采用机内净化技术和后处理技术相结合的处理方法。其中后处理方法改良是应对不断提高的标准的主要方式。后处理中的选择性催化还原技术(SelectiveCatalytic Reduction,SCR)具有去除效率高、成本低等优点,得到较多的关注。SCR技术就是指在催化剂存在的条件下,向烟气中喷入NH3、尿素或其他还原剂,使其选择性地与NOx反应生成N2,而不与O2发生非选择性氧化,从而达到降低NOx还原温度、提高NOx净化效率的目的。SCR技术的核心是催化性能出色的催化剂。NO x can cause air pollution problems such as smog, acid rain, and photochemical smog. It is an important air pollutant at present, and it is also a key object of air pollution prevention and control in China. Fossil fuel combustion brought about by people's industrial production and living activities is the main source of nitrogen oxides (NOx). Among anthropogenic NOx emissions, stationary sources such as coal-fired power plant flue gas and mobile sources such as diesel vehicle exhaust account for about 60% of the emissions. With the improvement of national emission regulations and standards, the combination of in-machine purification technology and post-treatment technology is required to meet the NOx emission standards of mobile sources. Among them, the improvement of post-processing method is the main way to deal with the rising standards. The selective catalytic reduction technology (SelectiveCatalytic Reduction, SCR) in post-treatment has the advantages of high removal efficiency and low cost, and has received more attention. SCR technology refers to spraying NH 3 , urea or other reducing agents into the flue gas in the presence of a catalyst to selectively react with NO x to generate N 2 instead of non-selective oxidation with O 2 . Therefore, the purpose of reducing the NOx reduction temperature and improving the NOx purification efficiency is achieved. The core of SCR technology is a catalyst with excellent catalytic performance.

目前在我国广泛推广应用的催化剂依然是V2O5-WO3(MoO3)/TiO2。该催化剂已广泛应用于固定源燃煤烟气脱硝,而且也被引入到柴油车尾气控制领域。但该催化剂体系用处柴油车尾气净化中尚有很多问题。为达标排放,在移动源尾气处理系统中,SCR处理系统往往需要与颗粒物捕集器(DPF)联用。如此,需要SCR催化剂能够承受DPF再生时带来的高温(高于700℃)和高湿度的环境,即催化剂需要具备优异的水热稳定性。但V2O5-WO3(MoO3)/TiO2催化剂在600℃以上会发生钒的挥发和载体TiO2的相变,所以该催化剂不适用于温度较高的机动车尾气处理,不能满足未来需求。另外钒的生物毒性也限制了它的使用。其他研究较为成熟的以ZSM-5、beta和Y等为载体制备的Cu基或Fe基等系列催化剂不同程度的存在温度操作窗口窄,水热稳定性差和抗HC中毒能力差等问题。因此,开发环保高效的NH3-SCR催化剂是非常急迫的。At present, the catalyst widely used in China is still V 2 O 5 -WO 3 (MoO 3 )/TiO 2 . The catalyst has been widely used in the denitrification of fixed-source coal-fired flue gas, and has also been introduced into the field of diesel vehicle exhaust control. However, there are still many problems in the application of the catalyst system in the purification of diesel vehicle exhaust. In order to meet emission standards, in the mobile source exhaust gas treatment system, the SCR treatment system often needs to be used in conjunction with a particulate filter (DPF). In this way, the SCR catalyst is required to be able to withstand the high temperature (higher than 700° C.) and high humidity environment brought about by DPF regeneration, that is, the catalyst needs to have excellent hydrothermal stability. However, the V 2 O 5 -WO 3 (MoO 3 )/TiO 2 catalyst will volatilize vanadium and phase change the carrier TiO 2 above 600°C, so this catalyst is not suitable for the treatment of motor vehicle exhaust at higher temperatures, and cannot meet the future needs. In addition, the biological toxicity of vanadium also limits its use. Other well-researched Cu-based or Fe-based catalysts prepared with ZSM-5, beta, and Y as supports have problems such as narrow temperature operating window, poor hydrothermal stability, and poor resistance to HC poisoning. Therefore, it is very urgent to develop environmentally friendly and efficient NH 3 -SCR catalysts.

小孔分子筛催化剂是目前NH3-SCR领域的研究热点,其中具有CHA结构的Cu-SAPO-34催化剂是该类分子筛催化剂的代表,该类催化剂同时具备高活性、高N2选择性和优异的水热稳定性。但该类催化剂对低温含水的环境较敏感,而且抗硫中毒能力较差,对实际应用不利。所以,进一步改良该催化剂是非常必要的。Small-pore molecular sieve catalysts are currently a research hotspot in the field of NH 3 -SCR. Among them, Cu-SAPO-34 catalyst with a CHA structure is a representative of this type of molecular sieve catalyst. This type of catalyst has high activity, high N 2 selectivity and excellent Hydrothermal stability. However, this type of catalyst is sensitive to low temperature and water-containing environment, and has poor resistance to sulfur poisoning, which is unfavorable for practical application. Therefore, it is necessary to further improve the catalyst.

2012100717231的专利公布了以液相离子交换法将Cu和Fe负载至SAPO-34载体上制备复合小孔分子筛催化剂用于NOx催化净化。但该方法步骤繁琐,需要多次负载,并且金属负载量不易控制。所得催化剂的低温抗水性能和抗硫中毒能力也没有相关报道。Patent No. 2012100717231 discloses that Cu and Fe are loaded onto SAPO-34 carrier by liquid-phase ion exchange method to prepare composite small-pore molecular sieve catalyst for catalytic purification of NOx. However, the steps of this method are cumbersome, multiple loads are required, and the amount of metal loading is not easy to control. The low-temperature water resistance and sulfur poisoning resistance of the obtained catalysts have not been reported.

发明内容Contents of the invention

为了解决上述问题,本发明的目的之一在于提供一种由原位合成法制备CuFe-SAPO-34催化剂的制备方法,催化剂通过水热合成法制得,为小孔分子筛类催化剂。本发明的方法简单易操作,所得催化剂具有优异的NH3-SCR催化性能,可以用于移动源NH3-SCR脱硝过程。此外,制备得到的选择性催化还原氮氧化物的催化剂,操作温度窗口宽,具有优异的N2生成选择性和水热稳定性的,非常适用于柴油车尾气中氮氧化物的净化。In order to solve the above problems, one of the objects of the present invention is to provide a method for preparing CuFe-SAPO-34 catalyst by in-situ synthesis method. The catalyst is prepared by hydrothermal synthesis method and is a small-pore molecular sieve catalyst. The method of the invention is simple and easy to operate, and the obtained catalyst has excellent NH 3 -SCR catalytic performance, and can be used in a mobile source NH 3 -SCR denitrification process. In addition, the prepared catalyst for selective catalytic reduction of nitrogen oxides has a wide operating temperature window, excellent N2 generation selectivity and hydrothermal stability, and is very suitable for the purification of nitrogen oxides in diesel vehicle exhaust.

本发明的原位合成法制备CuFe-SAPO-34催化剂的方法,是将铝源、水、磷源、硅源、Cu源、四乙烯五胺,和铁源混合搅拌均匀,然后加入模板剂,继续搅拌;将搅拌完全的凝胶装入水热反应釜中晶化,晶化反应结束后冷却;将固体结晶产物与母液分离,洗涤、干燥、焙烧,即得到CuFe-SAPO-34小孔分子筛催化剂。The method for preparing the CuFe-SAPO-34 catalyst by the in-situ synthesis method of the present invention is to mix and stir the aluminum source, water, phosphorus source, silicon source, Cu source, tetraethylenepentamine, and iron source evenly, and then add the templating agent, Continue to stir; put the fully stirred gel into a hydrothermal reaction kettle for crystallization, and cool after the crystallization reaction; separate the solid crystallization product from the mother liquor, wash, dry, and roast to obtain CuFe-SAPO-34 small-pore molecular sieve catalyst.

在一种实施方式中,所述铝源可以是拟薄水铝石AlOOH,三氧化二铝、偏铝酸钠等。In one embodiment, the aluminum source may be pseudoboehmite AlOOH, aluminum oxide, sodium metaaluminate, and the like.

在一种实施方式中,所述磷源为磷酸。In one embodiment, the phosphorus source is phosphoric acid.

在一种实施方式中,所述硅源为二氧化硅、硅溶胶等。In one embodiment, the silicon source is silicon dioxide, silica sol, and the like.

在一种实施方式中,所述Cu源为Cu盐。In one embodiment, the Cu source is a Cu salt.

在一种实施方式中,所述Cu盐为硫酸铜,硝酸铜、醋酸铜、氯化铜、碳酸铜、氧化铜等中的任意一种或者两种以上组合。In one embodiment, the Cu salt is any one or a combination of two or more of copper sulfate, copper nitrate, copper acetate, copper chloride, copper carbonate, copper oxide, and the like.

在一种实施方式中,所述铁源为铁盐。In one embodiment, the iron source is an iron salt.

在一种实施方式中,所述铁盐为硝酸铁、氯化铁、硫酸亚铁、硫酸铁、氯化亚铁、柠檬酸铁等中的任意一种或者两种以上组合。In one embodiment, the iron salt is any one of ferric nitrate, ferric chloride, ferrous sulfate, ferric sulfate, ferrous chloride, ferric citrate, or a combination of two or more.

在一种实施方式中,所述模板剂为正丙胺(C3H9N)、二乙胺、三乙胺、氢氧化四乙胺等中的任意一种或者两种以上组合。In one embodiment, the templating agent is any one or a combination of two or more of n-propylamine (C 3 H 9 N), diethylamine, triethylamine, tetraethylamine hydroxide, and the like.

在一种实施方式中,所述方法,具体包括如下步骤:In one embodiment, the method specifically includes the following steps:

(1)将拟薄水铝石加入去离子水中搅拌;(1) Pseudo-boehmite is added to deionized water and stirred;

(2)再加入磷酸,搅拌;(2) add phosphoric acid again, stir;

(3)加入气相法二氧化硅进行搅拌;(3) add fumed silicon dioxide and stir;

(4)将上述药品混合均匀后,加入Cu盐和四乙烯五胺;(4) After mixing the above medicines evenly, add Cu salt and tetraethylenepentamine;

(5)充分混合后,加入铁盐与正丙胺,继续搅拌。(5) After fully mixing, add iron salt and n-propylamine, and continue stirring.

(6)将搅拌完全的凝胶装入水热反应釜中晶化,晶化反应结束后冷却至室温。将固体结晶产物与母液分离,用去离子水洗涤至中性,干燥,然后在空气气氛中焙烧,即得到CuFe-SAPO-34小孔分子筛催化剂。(6) Put the fully stirred gel into a hydrothermal reaction kettle for crystallization, and cool to room temperature after the crystallization reaction is completed. The solid crystalline product is separated from the mother liquor, washed with deionized water until neutral, dried, and then calcined in an air atmosphere to obtain a CuFe-SAPO-34 small-pore molecular sieve catalyst.

在一种实施方式中,所述方法控制铝源、磷源、硅源、水、Cu源、四乙烯五胺、铁源、模板剂的摩尔比为(0.75-1.25):(0.75-1.25):(0.4-0.7):(70-80):(0.01-3.5):(0.01-3.5):(0.001-0.1):(0.01-3.5)。In one embodiment, the method controls the molar ratio of aluminum source, phosphorus source, silicon source, water, Cu source, tetraethylenepentamine, iron source, and templating agent to be (0.75-1.25): (0.75-1.25) :(0.4-0.7):(70-80):(0.01-3.5):(0.01-3.5):(0.001-0.1):(0.01-3.5).

在一种实施方式中,所述方法控制铝源、磷源、硅源、水、Cu源、四乙烯五胺、铁源、模板剂的摩尔比为1:1:0.57:77.17:0.12:0.12:(0.019-0.076):3.38。In one embodiment, the method controls the molar ratio of aluminum source, phosphorus source, silicon source, water, Cu source, tetraethylenepentamine, iron source, and templating agent to be 1:1:0.57:77.17:0.12:0.12 :(0.019-0.076): 3.38.

在一种实施方式中,所述铝源、磷源、硅源、水、Cu源、四乙烯五胺、铁源、模板剂分别为AlOOH、H3PO4、SiO2、H2O、Cu盐、四乙烯五胺、Fe盐和正丙胺。In one embodiment, the aluminum source, phosphorus source, silicon source, water, Cu source, tetraethylenepentamine, iron source, template agent are respectively AlOOH, H 3 PO 4 , SiO 2 , H 2 O, Cu salt, tetraethylenepentamine, Fe salt and n-propylamine.

在一种实施方式中,AlOOH、H3PO4、SiO2、H2O、Cu盐、四乙烯五胺、Fe盐和正丙胺的摩尔比为1:1:0.57:77.17:0.12:0.12:0.057:3.38。In one embodiment, the molar ratio of AlOOH, H 3 PO 4 , SiO 2 , H 2 O, Cu salt, tetraethylenepentamine, Fe salt and n-propylamine is 1:1:0.57:77.17:0.12:0.12:0.057 : 3.38.

在一种实施方式中,晶化反应的温度为150-200℃,如150、155、160、165、170、175、180、185、190、195或200℃。In one embodiment, the temperature of the crystallization reaction is 150-200°C, such as 150, 155, 160, 165, 170, 175, 180, 185, 190, 195 or 200°C.

在一种实施方式中,所述晶化反应的时间为24-72h,如30、35、40、45、50、55、60、65、72h。In one embodiment, the crystallization reaction time is 24-72 hours, such as 30, 35, 40, 45, 50, 55, 60, 65, 72 hours.

在一种实施方式中,所述晶化反应的时间为72h。In one embodiment, the crystallization reaction time is 72 hours.

在一种实施方式中,所述洗涤是用水洗涤至中性。In one embodiment, the washing is to neutral with water.

在一种实施方式中,所述干燥的温度为80-120℃,如80℃、90℃、100℃、110℃、120℃。In one embodiment, the drying temperature is 80-120°C, such as 80°C, 90°C, 100°C, 110°C, 120°C.

在一种实施方式中,所述干燥的温度为100℃。In one embodiment, the drying temperature is 100°C.

在一种实施方式中,所述干燥的时间为3-16小时,如3h、5h、6h、8h、10h、12h、16h。In one embodiment, the drying time is 3-16 hours, such as 3h, 5h, 6h, 8h, 10h, 12h, 16h.

在一种实施方式中,所述干燥的时间为12h。In one embodiment, the drying time is 12 hours.

在一种实施方式中,所述焙烧是在空气气氛中焙烧。In one embodiment, the calcination is calcination in an air atmosphere.

在一种实施方式中,所述焙烧的温度为550-800℃,如550℃、600℃、650℃、700℃、800℃。In one embodiment, the calcination temperature is 550-800°C, such as 550°C, 600°C, 650°C, 700°C, 800°C.

在一种实施方式中,所述焙烧的温度为600℃。In one embodiment, the calcination temperature is 600°C.

在一种实施方式中,所述焙烧的时间为3-10小时,如3h、5h、6h、8h、10h。In one embodiment, the calcination time is 3-10 hours, such as 3h, 5h, 6h, 8h, 10h.

在一种实施方式中,所述焙烧的时间为6h。In one embodiment, the calcination time is 6 hours.

在一种实施方式中,所述焙烧的升温速率为0.5-5℃/min,例如,0.5、1、1.5、2、2.5、3、3.5、4、4.5、5℃/min。In one embodiment, the heating rate of the calcination is 0.5-5° C./min, for example, 0.5, 1, 1.5, 2, 2.5, 3, 3.5, 4, 4.5, 5° C./min.

在一种实施方式中,所述焙烧升温速率为1℃/min。In one embodiment, the heating rate of the calcination is 1° C./min.

在一种实施方式中,所述方法具体包括以下步骤:将拟薄水铝石加入去离子水中进行搅拌,然后加入正磷酸和气相法二氧化硅,待混匀后加入铜盐和四乙烯五胺,充分搅拌后加入Fe盐和正丙胺;将搅拌完全的凝胶装入水热反应釜中晶化,晶化反应完成后冷却至室温,将固体结晶产物与母液分离,用去离子水洗涤至中性,干燥,然后在空气中焙烧,得到CuFe-SAPO-34小孔分子筛催化剂;其中控制AlOOH、H3PO4、SiO2、H2O、Cu盐、四乙烯五胺、Fe盐和正丙胺的摩尔比为1:1:0.57:77.17:0.12:0.019-0.076:3.38。采用该方案所得催化剂具有优异的催化活性,其在300-500℃内具有高于80%的NOx转化率,并且显著提高了Cu-SAPO-34的低温抗水性能。In one embodiment, the method specifically includes the following steps: adding pseudo-boehmite to deionized water for stirring, then adding orthophosphoric acid and fumed silica, and adding copper salt and tetraethylenepenta Amine, after fully stirring, add Fe salt and n-propylamine; put the fully stirred gel into a hydrothermal reaction kettle for crystallization, cool to room temperature after the crystallization reaction is completed, separate the solid crystallization product from the mother liquor, and wash with deionized water until Neutral, dry, and then calcined in air to obtain CuFe-SAPO-34 small-pore molecular sieve catalyst; in which control AlOOH, H 3 PO 4 , SiO 2 , H 2 O, Cu salt, tetraethylenepentamine, Fe salt and n-propylamine The molar ratio is 1:1:0.57:77.17:0.12:0.019-0.076:3.38. The catalyst obtained by adopting this scheme has excellent catalytic activity, which has a NOx conversion rate higher than 80% within 300-500° C., and significantly improves the low-temperature water resistance of Cu-SAPO-34.

本发明的第二个目的是提供按照上述方法制备得到的CuFe-SAPO-34小孔分子筛催化剂。The second object of the present invention is to provide the CuFe-SAPO-34 small-pore molecular sieve catalyst prepared according to the above method.

本发明的第三个目的是提供所述CuFe-SAPO-34小孔分子筛催化剂的应用。The third object of the present invention is to provide the application of the CuFe-SAPO-34 small-pore molecular sieve catalyst.

在一种实施方式中,所述应用是用于催化氮氧化物。In one embodiment, the use is for catalyzing nitrogen oxides.

在一种实施方式中,所述应用是用于NH3-SCR反应。In one embodiment, the application is for NH 3 -SCR reactions.

在一种实施方式中,所述应用是催化还原柴油车尾气中氮氧化物。In one embodiment, the application is catalytic reduction of nitrogen oxides in diesel vehicle exhaust.

本发明的有益效果:Beneficial effects of the present invention:

(1)本方法采用原位合成法制备CuFe-SAPO-34小孔分子筛催化剂,并进一步通过控制Fe盐的投入量来控制Fe盐的负载量,以得到NH3-SCR催化活性及抗水稳定性优异的分子筛催化剂;所述CuFe-SAPO-34的制备方法为一步合成法,相比目前使用的液相离子交换法更为简单有效,无需多步离子交换步骤,节约资源。(1) This method adopts the in-situ synthesis method to prepare CuFe-SAPO-34 small-pore molecular sieve catalyst, and further controls the loading amount of Fe salt by controlling the input amount of Fe salt to obtain NH 3 -SCR catalytic activity and water-resistant stability Molecular sieve catalyst with excellent properties; the preparation method of CuFe-SAPO-34 is a one-step synthesis method, which is simpler and more effective than the currently used liquid phase ion exchange method, and does not require multiple ion exchange steps, saving resources.

(2)该方法制备所得催化剂利用Cu和Fe之间的协同效应,使催化剂的温度窗口拓宽,特别是高温段活性的提高更为显著,更加适用于柴油车尾气净化。(2) The catalyst prepared by this method utilizes the synergistic effect between Cu and Fe to widen the temperature window of the catalyst, especially the activity at high temperature is more significantly improved, and is more suitable for diesel vehicle exhaust purification.

(3)该方法制备的催化剂提高了其低温抗水能力。(3) The catalyst prepared by this method has improved its low temperature water resistance.

(4)该方法制备的催化剂提高了抗硫中毒能力。(4) The catalyst prepared by this method has improved resistance to sulfur poisoning.

(5)本发明的催化剂采用无毒组分制备,不会对人体健康和生态环境造成危害;制备方法简单易操作。(5) The catalyst of the present invention is prepared by using non-toxic components, which will not cause harm to human health and ecological environment; the preparation method is simple and easy to operate.

附图说明Description of drawings

图1为本发明制备的CuFe-SAPO-34和Cu-SAPO-34的催化剂活性及抗水中毒能力比较;Fig. 1 is that the catalytic activity of CuFe-SAPO-34 and Cu-SAPO-34 prepared by the present invention and the water intoxication resistance compare;

图2为本发明制备的CuFe-SAPO-34和Cu-SAPO-34催化剂抗硫中毒能力的变化。Fig. 2 is the variation of anti-sulfur poisoning ability of CuFe-SAPO-34 and Cu-SAPO-34 catalysts prepared by the present invention.

具体实施方案specific implementation plan

在本发明中,催化剂的评价采取如下方法:In the present invention, the evaluation of catalyst takes following method:

取CuFe-SAPO-34分子筛催化剂,放置在活性评价固定床反应器上,模拟废气组成为500ppm NH3、500ppm NO、5vol%O2,N2为平衡气,总流量为500mL/min,反应空速为400000h-1Take the CuFe-SAPO-34 molecular sieve catalyst and place it on a fixed-bed reactor for activity evaluation. The simulated waste gas composition is 500ppm NH 3 , 500ppm NO, 5vol% O 2 , N 2 is the balance gas, and the total flow rate is 500mL/min. The speed is 400000h -1 .

下面是对本发明进行具体描述。The following is a detailed description of the present invention.

实施例1Example 1

以拟薄水铝石AlOOH为铝源,二氧化硅(SiO2)为硅源,磷酸(H3PO4)为磷源,Cu-TEPA为Cu源、Fe(NO3)3·9H2O为铁源,将各原料混合,然后添加正丙胺(C3H9N)为模板剂,搅拌过夜直到搅拌均匀;再将溶液放入反应釜中,将反应釜放入180℃的烘箱中晶化3d;待反应釜充分冷却后,搅拌静置并滤除杂质后抽滤,将抽虑后的样品放入105℃的烘箱3h将其烘干;再将烘干的样品放入马弗炉中,以1℃/min的升温速度升至600℃焙烧6h,得到一步合成法制备的CuFe-SAPO-34催化剂。其中,控制AlOOH、H3PO4、SiO2、H2O、Cu盐、四乙烯五胺、Fe盐和正丙胺的摩尔比为1:1:0.57:77.17:0.12::0.12:0.057:3.38。Pseudoboehmite AlOOH is used as aluminum source, silicon dioxide (SiO 2 ) is used as silicon source, phosphoric acid (H 3 PO 4 ) is used as phosphorus source, Cu-TEPA is used as Cu source, Fe(NO 3 ) 3 ·9H 2 O As the iron source, mix the raw materials, then add n-propylamine (C 3 H 9 N) as the template agent, stir overnight until the stirring is uniform; then put the solution into the reaction kettle, and put the reaction kettle into an oven at 180°C to crystallize After 3 days; after the reactor is fully cooled, stir and stand still and filter out impurities, then filter with suction, put the filtered sample in an oven at 105°C for 3 hours to dry it; then put the dried sample into a muffle furnace In the process, the temperature was raised to 600°C for 6 hours at a rate of 1°C/min to obtain a CuFe-SAPO-34 catalyst prepared by a one-step synthesis method. Among them, the molar ratio of AlOOH, H 3 PO 4 , SiO 2 , H 2 O, Cu salt, tetraethylenepentamine, Fe salt and n-propylamine is controlled to be 1:1:0.57:77.17:0.12::0.12:0.057:3.38.

对照:不添加Fe盐,按照上述制备方法,可制得Cu-SAPO-34催化剂。Control: Cu-SAPO-34 catalyst can be prepared according to the above preparation method without adding Fe salt.

为考察添加Fe盐前后,催化剂的低温抗水能力变化,将催化剂在含10%H2O的空气气氛中,经70℃老化16h,检测老化前后的催化剂性能变化。图1给出Fe盐添加前后催化剂性能变化In order to investigate the change of the low-temperature water resistance of the catalyst before and after the addition of Fe salt, the catalyst was aged at 70°C for 16 hours in an air atmosphere containing 10% H 2 O, and the performance change of the catalyst before and after aging was detected. Figure 1 shows the change in catalyst performance before and after Fe salt addition

从图1中可以看出,CuFe-SAPO-34催化剂的温度窗口较宽,可在250-550℃范围内保持大于70%的NOx转化率,最高活性可达到90.3%。而对照Cu-SAPO-34的温度窗口较窄,仅能在250-350℃范围内保持大于60%的NOx转化率,最高活性可达到78.6%。It can be seen from Figure 1 that the CuFe-SAPO-34 catalyst has a wide temperature window, and can maintain a NOx conversion rate greater than 70% in the range of 250-550 °C, and the highest activity can reach 90.3%. The control Cu-SAPO-34 has a narrow temperature window, and can only maintain a NOx conversion rate greater than 60% in the range of 250-350°C, and the highest activity can reach 78.6%.

此外,CuFe-SAPO-34经70℃老化16h后,催化剂仍可在300-500℃范围内保持大于50%的NOx转化率。而对照Cu-SAPO-34经相同老化条件处理后,仅在300-450℃范围内保持大于30%的NOx转化率。In addition, after CuFe-SAPO-34 was aged at 70°C for 16h, the catalyst could still maintain more than 50% NOx conversion in the range of 300-500°C. However, after the control Cu-SAPO-34 was treated under the same aging conditions, it only maintained a NOx conversion rate greater than 30% in the range of 300-450°C.

由以上数据,可知本方法不仅提高催化剂的活性,还显著提高其低温抗水性能。From the above data, it can be seen that this method not only improves the activity of the catalyst, but also significantly improves its low-temperature water resistance.

图2给出Fe加入前后催化剂的抗硫中毒能力的情况,可知硫中毒后的CuFe-SAPO-34催化剂仍可在350-500℃保留大于60%的转化率,最高NOx转化率为81.5%。但Cu-SAPO-34催化剂仅在400-500℃保留大于60%的转化率,最高NOx转化率为62.9%。Figure 2 shows the anti-sulfur poisoning ability of the catalyst before and after Fe addition. It can be seen that the CuFe-SAPO-34 catalyst after sulfur poisoning can still retain a conversion rate of more than 60% at 350-500 °C, and the highest NOx conversion rate is 81.5%. But the Cu-SAPO-34 catalyst only retains more than 60% conversion at 400-500°C, and the highest NOx conversion is 62.9%.

实施例2Example 2

本实施例考察了不同Fe盐添加量下得到的CuFe-SAPO-34催化剂的性能。In this example, the performance of CuFe-SAPO-34 catalysts obtained under different Fe salt additions was investigated.

催化剂的制备方法:调整Fe的投加量,控制AlOOH、H3PO4、SiO2、H2O、Cu盐、四乙烯五胺、Fe盐和正丙胺的摩尔比分别为A(1:1:0.57:77.17:0.12:0.12:0.0095:3.38)、B(1:1:0.57:77.17:0.12:0.12:0.019:3.38)、C(1:1:0.57:77.17:0.12:0.12:0.029:3.38)、D(1:1:0.57:77.17:0.12:0.12:0.043:3.38)。其余与实施例1相同。The preparation method of the catalyst: adjust the dosage of Fe, control the molar ratio of AlOOH, H 3 PO 4 , SiO 2 , H 2 O, Cu salt, tetraethylenepentamine, Fe salt and n-propylamine to A (1:1: 0.57:77.17:0.12:0.12:0.0095:3.38), B(1:1:0.57:77.17:0.12:0.12:0.019:3.38), C(1:1:0.57:77.17:0.12:0.12:0.029:3.38) , D(1:1:0.57:77.17:0.12:0.12:0.043:3.38). All the other are identical with embodiment 1.

制备得到的CuFe-SAPO-34催化剂,在不同温度下的催化性能如表1所示。The catalytic properties of the prepared CuFe-SAPO-34 catalyst at different temperatures are shown in Table 1.

表1不同Fe添加量下得到的催化剂的催化性能Catalytic properties of catalysts obtained under different Fe additions in table 1

实施例3Example 3

本实施例考察了不同晶化温度下得到的CuFe-SAPO-34催化剂的性能。In this example, the properties of CuFe-SAPO-34 catalysts obtained at different crystallization temperatures were investigated.

控制AlOOH、H3PO4、SiO2、H2O、Cu盐、四乙烯五胺、Fe盐和正丙胺的摩尔比为1:1:0.57:77.17:0.12::0.12:0.057:3.38,晶化温度分别为150℃、200℃,其余与实施例1相同。制备得到的CuFe-SAPO-34催化剂的性能如表2所示。Control the molar ratio of AlOOH, H 3 PO 4 , SiO 2 , H 2 O, Cu salt, tetraethylenepentamine, Fe salt and n-propylamine to 1:1:0.57:77.17:0.12::0.12:0.057:3.38, crystallization The temperature is respectively 150°C and 200°C, and the rest are the same as in Example 1. The properties of the prepared CuFe-SAPO-34 catalyst are shown in Table 2.

表2不同晶化温度下得到的催化剂的催化性能The catalytic performance of the catalyst obtained under the different crystallization temperature of table 2

虽然本发明已以较佳实施例公开如上,但其并非用以限定本发明,任何熟悉此技术的人,在不脱离本发明的精神和范围内,都可做各种的改动与修饰,因此本发明的保护范围应该以权利要求书所界定的为准。Although the present invention has been disclosed above with preferred embodiments, it is not intended to limit the present invention. Any person familiar with this technology can make various changes and modifications without departing from the spirit and scope of the present invention. Therefore The scope of protection of the present invention should be defined by the claims.

Claims (10)

1. a kind of method that in-situ synthesis prepares CuFe-SAPO-34 catalyst, it is characterised in that methods described be by silicon source, Phosphorus source, silicon source, water, Cu sources, TEPA, and source of iron are mixed evenly, and then add template, continue to stir;It will stir Mix complete gel and be fitted into crystallization in hydrothermal reaction kettle, crystallization is cooled down after terminating;Solid crystallized product is separated with mother liquor, Washing, dry, roasting, that is, obtain CuFe-SAPO-34 small pore molecular sieve catalysts.
2. according to the method described in claim 1, it is characterised in that methods described control silicon source, phosphorus source, silicon source, water, Cu sources, TEPA, source of iron, the mol ratio of template are (0.75-1.25):(0.75-1.25):(0.4-0.7):(70-80): (0.01-3.5):(0.01-3.5):(0.001-0.1):(0.01-3.5).
3. according to the method described in claim 1, it is characterised in that methods described control silicon source, phosphorus source, silicon source, water, Cu sources, TEPA, source of iron, the mol ratio of template are 1:1:0.57:77.17:0.12:0.12:(0.019-0.076):3.38.
4. according to the method described in claim 1, it is characterised in that source of aluminium is boehmite AlOOH, alundum (Al2O3) Or sodium metaaluminate.
5. according to the method described in claim 1, it is characterised in that the source of iron is molysite, such as ferric nitrate, iron chloride, sulphur Any one in sour ferrous iron, ferric sulfate, frerrous chloride, ironic citrate or two or more combinations.
6. according to the method described in claim 1, it is characterised in that the Cu sources are Cu salt, such as copper sulphate, copper nitrate, vinegar Any one in sour copper, copper chloride, copper carbonate, cupric oxide or two or more combinations.
7. according to the method described in claim 1, it is characterised in that the temperature of crystallization is 150-200 DEG C.
8. the CuFe-SAPO-34 catalyst prepared according to any methods described of claim 1~7.
9. the application of CuFe-SAPO-34 catalyst described in claim 8.
10. application according to claim 9, it is characterised in that for NH3- SCR reacts.
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