CN114054020B - Perovskite structure material and application thereof in formaldehyde removal at room temperature - Google Patents
Perovskite structure material and application thereof in formaldehyde removal at room temperature Download PDFInfo
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Abstract
Description
技术领域Technical Field
本发明属于环境催化领域,尤其涉及一种钙钛矿结构材料及其在室温去除甲醛中的应用。The invention belongs to the field of environmental catalysis, and in particular relates to a perovskite structure material and an application thereof in removing formaldehyde at room temperature.
背景技术Background Art
甲醛是一种由家具、纺织物、装修材料等释放的有刺激性气味的气体,是局部空间里主要的污染物之一。世界卫生组织国际癌症研究机构将甲醛列为第一类致癌物质,长期暴露于低浓度的甲醛会引起健康问题。Formaldehyde is a pungent gas released by furniture, textiles, and decoration materials. It is one of the main pollutants in local spaces. The World Health Organization's International Agency for Research on Cancer lists formaldehyde as a Class I carcinogen. Long-term exposure to low concentrations of formaldehyde can cause health problems.
现有的去除甲醛的技术有吸附法、等离子体技术、光催化法和热催化法,但存在吸附剂饱和、产生副产物、效率低、需要能量等缺点。室温催化氧化技术是在室温下将甲醛催化氧化分解为二氧化碳和水,是去除甲醛的有效方法。Existing technologies for removing formaldehyde include adsorption, plasma technology, photocatalysis and thermal catalysis, but they have disadvantages such as adsorbent saturation, by-product generation, low efficiency and energy requirements. Room temperature catalytic oxidation technology is an effective method for removing formaldehyde by catalytically oxidizing formaldehyde into carbon dioxide and water at room temperature.
根据文献报道,能够在室温有效去除甲醛的催化剂主要有负载型贵金属Pt催化剂(Applied Surface Science,2017,411,105-112;Angewandte Chemie.InternationalEd.in English,2021,60(12):6377-6381)、Au催化剂(Environmental Science&Technology,2014,48(16):9702-9708;.Applied Catalysis B:Environmental,2020,268:118461-118466)和Ag催化剂(Catalysis Today,2016,277,257-265)等。CN 102240549 A公开了一种高效抗湿室温去除甲醛的催化技术,以蜂窝陶瓷为载体,先负载孔道掺杂Ag的MnO2,再负载贵金属Pt为活性组分。但是,由于贵金属总量有限,价格高,严重制约了贵金属催化剂在实际中的应用。According to literature reports, catalysts that can effectively remove formaldehyde at room temperature mainly include supported precious metal Pt catalysts (Applied Surface Science, 2017, 411, 105-112; Angewandte Chemie. International Ed. in English, 2021, 60 (12): 6377-6381), Au catalysts (Environmental Science & Technology, 2014, 48 (16): 9702-9708; Applied Catalysis B: Environmental, 2020, 268: 118461-118466) and Ag catalysts (Catalysis Today, 2016, 277, 257-265), etc. CN 102240549 A discloses a catalytic technology for removing formaldehyde at room temperature with high efficiency and moisture resistance, using honeycomb ceramics as a carrier, first loading pore-doped Ag-doped MnO 2 , and then loading precious metal Pt as an active component. However, the limited total amount and high price of precious metals severely restrict the practical application of precious metal catalysts.
而过渡金属因为成本低的优点被广泛研究,但空气中含有的水汽对催化剂活性及稳定性产生影响,随着湿度的增加,甲醛的转化率下降。如室温下尖晶石MnCo2O4催化剂上甲醛的转化率随着湿度的增加而下降,2小时内完全失活(Applied Catalysis B:Environmental,2019,254,76-85.)。99℃时在ε-MnO2上,水的加入(相对湿度为46%)使甲醛的转化率由约60%下降至49%(Chemical Engineering Journal 2020,388.124146-124157)。在室温下MnO2催化剂上,水的加入(相对湿度为38%)使甲醛的初始转化率由45%下降至12%,且50分钟完全失活(Journal of Hazardous Materials,2021,414,125542-125552)。在MnOx–CeO2混合氧化物催化剂上也观察到随着湿度的增加甲醛转化率降低的现象(Applied Catalysis B:Environmental 2006,62(3-4),265-273.)。而MnO2催化剂到11小时才能实现200ppm甲醛完全转化为CO2和H2O(Environmental Science&Technology,2015,49(20):12372-12379)。Transition metals have been widely studied because of their low cost, but the water vapor in the air affects the activity and stability of the catalyst. As the humidity increases, the conversion rate of formaldehyde decreases. For example, the conversion rate of formaldehyde on the spinel MnCo 2 O 4 catalyst decreases with increasing humidity at room temperature and is completely deactivated within 2 hours (Applied Catalysis B: Environmental, 2019, 254, 76-85.). At 99°C on ε-MnO 2 , the addition of water (relative humidity of 46%) reduces the conversion rate of formaldehyde from about 60% to 49% (Chemical Engineering Journal 2020, 388.124146-124157). At room temperature, the addition of water (relative humidity of 38%) on the MnO2 catalyst reduced the initial formaldehyde conversion rate from 45% to 12%, and it was completely deactivated in 50 minutes (Journal of Hazardous Materials, 2021, 414, 125542-125552). The phenomenon of decreased formaldehyde conversion rate with increasing humidity was also observed on the MnOx - CeO2 mixed oxide catalyst (Applied Catalysis B: Environmental 2006, 62 (3-4), 265-273.). However, it took 11 hours for the MnO2 catalyst to completely convert 200 ppm formaldehyde into CO2 and H2O (Environmental Science & Technology, 2015, 49 (20): 12372-12379).
因此,在存在环境湿度的室温条件下实现快速且稳定地将甲醛转化为CO2和H2O仍然是一个挑战。Therefore, achieving rapid and stable conversion of formaldehyde to CO2 and H2O at room temperature in the presence of ambient humidity remains a challenge.
发明内容Summary of the invention
本发明的目的是提供一种钙钛矿结构材料及其在室温去除甲醛中的应用,该钙钛矿结构材料为具有钙钛矿结构的MMnO3催化剂,M金属为铜、锌、铁、镍中的一种或两种,在环境湿度下能快速和稳定的将甲醛完全氧化成CO2和H2O,适用湿度范围广,且制备方法简单,成本比贵金属催化剂低,催化反应时不需要外部能量输入,适用于存在环境湿度的居家、车内、办公等封闭、半封闭的甲醛污染去除。The purpose of the present invention is to provide a perovskite structure material and its application in removing formaldehyde at room temperature. The perovskite structure material is a MMnO3 catalyst with a perovskite structure, and the M metal is one or two of copper, zinc, iron, and nickel. The formaldehyde can be quickly and stably completely oxidized into CO2 and H2O under ambient humidity. The applicable humidity range is wide, and the preparation method is simple. The cost is lower than that of precious metal catalysts. No external energy input is required during the catalytic reaction. The perovskite structure material is suitable for removing formaldehyde pollution in closed and semi-closed places such as homes, cars, and offices where ambient humidity exists.
第一方面,本发明提供一种钙钛矿结构材料,具有如下化学通式:MMnO3,其中,M金属为铜、锌、铁、镍中的一种或两种组合。所述组合示例性的包括铜和锌组合、铜和铁组合、铜和镍组合、锌和铁组合、锌和镍组合、铁和镍组合等。In a first aspect, the present invention provides a perovskite structure material having the following general chemical formula: MMnO 3 , wherein the metal M is one or a combination of two of copper, zinc, iron, and nickel. The combination exemplarily includes a combination of copper and zinc, a combination of copper and iron, a combination of copper and nickel, a combination of zinc and iron, a combination of zinc and nickel, a combination of iron and nickel, and the like.
上述的钙钛矿结构材料中,所述M金属可为铜和锌组合,优选地,铜和锌的摩尔比为x:(1-x),x=0.01~0.99,例如0.01:0.99、0.10:0.90、0.30:0.70、0.45:0.55、0.50:0.50、0.65:0.35、0.80:0.20等。In the above-mentioned perovskite structural material, the M metal may be a combination of copper and zinc. Preferably, the molar ratio of copper to zinc is x:(1-x), x=0.01-0.99, for example, 0.01:0.99, 0.10:0.90, 0.30:0.70, 0.45:0.55, 0.50:0.50, 0.65:0.35, 0.80:0.20, etc.
上述的钙钛矿结构材料中,所述M金属可为铜和铁组合,优选地,铜和铁的摩尔比为x:(1-x),x=0.02~0.98,例如0.02:0.98、0.20:0.80、0.30:0.70、0.45:0.55、0.50:0.50、0.70:0.30、0.85:0.15等。In the above-mentioned perovskite structural material, the M metal may be a combination of copper and iron. Preferably, the molar ratio of copper to iron is x:(1-x), x=0.02~0.98, for example, 0.02:0.98, 0.20:0.80, 0.30:0.70, 0.45:0.55, 0.50:0.50, 0.70:0.30, 0.85:0.15, etc.
上述的钙钛矿结构材料中,所述M金属为铜和镍组合,优选地,铜和镍的摩尔比为x:(1-x),x=0.1~0.9,例如0.10:0.90、0.20:0.80、0.30:0.70、0.50:0.50、0.80:0.20、0.90:0.10等。In the above-mentioned perovskite structural material, the M metal is a combination of copper and nickel. Preferably, the molar ratio of copper to nickel is x:(1-x), x=0.1~0.9, for example 0.10:0.90, 0.20:0.80, 0.30:0.70, 0.50:0.50, 0.80:0.20, 0.90:0.10, etc.
上述的钙钛矿结构材料中,所述的M金属为锌和铁组合,优选地,锌和铁的摩尔比为x:(1-x),x=0.05~0.95,例如0.05:0.95、0.10:0.90、0.35:0.65、0.45:0.55、0.50:0.50、0.80:0.20、0.95:0.05等。In the above-mentioned perovskite structural material, the M metal is a combination of zinc and iron. Preferably, the molar ratio of zinc to iron is x:(1-x), x=0.05~0.95, for example, 0.05:0.95, 0.10:0.90, 0.35:0.65, 0.45:0.55, 0.50:0.50, 0.80:0.20, 0.95:0.05, etc.
上述的钙钛矿结构材料中,所述M金属为锌和镍组合,优选地,锌和镍的摩尔比为x:(1-x),x=0.2~0.8,例如0.20:0.80、0.30:0.70、0.45:0.55、0.50:0.50、0.6:0.4、0.80:0.20等。In the above-mentioned perovskite structural material, the M metal is a combination of zinc and nickel. Preferably, the molar ratio of zinc to nickel is x:(1-x), x=0.2~0.8, for example 0.20:0.80, 0.30:0.70, 0.45:0.55, 0.50:0.50, 0.6:0.4, 0.80:0.20, etc.
上述的钙钛矿结构材料中,所述的M金属为铁和镍组合,优选地,铁和镍的摩尔比为x:(1-x),x=0.15~0.85,例如0.15:0.85、0.20:0.80、0.30:0.70、0.45:0.55、0.50:0.50、0.80:0.20、0.85:0.15等。In the above-mentioned perovskite structural material, the M metal is a combination of iron and nickel. Preferably, the molar ratio of iron to nickel is x:(1-x), x=0.15~0.85, for example, 0.15:0.85, 0.20:0.80, 0.30:0.70, 0.45:0.55, 0.50:0.50, 0.80:0.20, 0.85:0.15, etc.
所述钙钛矿结构材料的制备方法,包括如下步骤:The method for preparing the perovskite structure material comprises the following steps:
(1)将锰盐的水溶液与所述M金属的金属盐的水溶液混合,得到金属盐溶液;(1) mixing an aqueous solution of a manganese salt with an aqueous solution of a metal salt of the M metal to obtain a metal salt solution;
(2)将碳酸氢盐的水溶液与所述金属盐溶液混合进行共沉淀,得到沉淀;(2) mixing the aqueous solution of bicarbonate with the metal salt solution for co-precipitation to obtain a precipitate;
(3)将所述沉淀干燥后进行焙烧,得到所述钙钛矿结构材料。(3) Drying the precipitate and then calcining it to obtain the perovskite structure material.
步骤(1)中,所述锰盐可为任意可溶于水的锰盐,如硝酸锰;In step (1), the manganese salt may be any water-soluble manganese salt, such as manganese nitrate;
所述M金属的金属盐可为任意可溶于水的M金属的金属盐,如硝酸M盐;The metal salt of the M metal may be any water-soluble metal salt of the M metal, such as nitrate M salt;
所述锰盐的水溶液与所述M金属的金属盐的水溶液的比例控制在锰与M金属的摩尔比为1:5~5:1,具体可为1:1;The ratio of the aqueous solution of the manganese salt to the aqueous solution of the metal salt of the M metal is controlled so that the molar ratio of manganese to M metal is 1:5 to 5:1, specifically 1:1;
例如,所述锰盐的水溶液的浓度可为0.1mmol/L~200mmol/L,具体可为50mmol/L;For example, the concentration of the aqueous solution of the manganese salt may be 0.1 mmol/L to 200 mmol/L, specifically 50 mmol/L;
所述M金属的金属盐的水溶液的浓度可为0.1mmol/L~200mmol/L,具体可为50mmol/L;The concentration of the aqueous solution of the metal salt of the M metal may be 0.1 mmol/L to 200 mmol/L, specifically 50 mmol/L;
所述锰盐的水溶液与所述M金属的金属盐的水溶液的体积比可为1:9~9:1,具体可为1:1。The volume ratio of the aqueous solution of the manganese salt to the aqueous solution of the metal salt of the M metal may be 1:9 to 9:1, specifically 1:1.
步骤(2)中,所述碳酸氢盐的浓度可为0.1mmol/L~500mmol/L,具体可为36mmol/L;In step (2), the concentration of the bicarbonate may be 0.1 mmol/L to 500 mmol/L, specifically 36 mmol/L;
所述碳酸氢盐可为NH4HCO3、KHCO3、NaHCO3中的任一种;The bicarbonate may be any one of NH 4 HCO 3 , KHCO 3 , and NaHCO 3 ;
所述碳酸氢盐的水溶液与所述金属盐溶液的体积比可为1:9~9:1,具体可为1:1。The volume ratio of the aqueous solution of bicarbonate to the metal salt solution may be 1:9 to 9:1, specifically 1:1.
步骤(2)中,所述共沉淀的温度具体可为室温(15~30℃),时间具体可为12小时;In step (2), the coprecipitation temperature may be room temperature (15-30° C.) and the coprecipitation time may be 12 hours;
所述共沉淀在搅拌条件下进行;The coprecipitation is carried out under stirring conditions;
所述方法在所述共沉淀后还包括对沉淀进行洗涤的步骤,如用超纯水和无水乙醇多次洗涤沉淀。The method further comprises a step of washing the precipitate after the coprecipitation, such as washing the precipitate with ultrapure water and anhydrous ethanol for multiple times.
步骤(3)中,所述干燥的温度可为60℃~100℃,具体可为60℃;时间可为1~12h,具体可为6h;In step (3), the drying temperature may be 60° C. to 100° C., specifically 60° C.; the drying time may be 1 to 12 hours, specifically 6 hours;
所述焙烧在空气中进行;The calcination is carried out in air;
所述焙烧的温度可为120~550℃,具体可为350℃;The calcination temperature may be 120-550°C, specifically 350°C;
所述焙烧的时间可为1~10小时,具体可为4小时。The calcination time may be 1 to 10 hours, specifically 4 hours.
第二方面,本发明提供上述的钙钛矿结构材料在存在环境湿度的室温条件下去除甲醛中的应用或制备室温去除甲醛的耐湿催化剂中的应用。In a second aspect, the present invention provides the use of the above-mentioned perovskite structure material in removing formaldehyde at room temperature in the presence of ambient humidity or in preparing a moisture-resistant catalyst for removing formaldehyde at room temperature.
所述钙钛矿结构材料中M金属与Mn金属通过氧原子连接而产生协同作用,使得所述催化剂具有H2O亲和性。The M metal and the Mn metal in the perovskite structure material are connected by oxygen atoms to produce a synergistic effect, so that the catalyst has H 2 O affinity.
所述去除甲醛的环境中的湿度可为0%~90%,优选为40%~65%。The humidity in the formaldehyde removal environment may be 0% to 90%, preferably 40% to 65%.
所述去除甲醛的环境中甲醛的浓度可为2~200ppm。The concentration of formaldehyde in the formaldehyde removal environment may be 2 to 200 ppm.
第三方面,本发明提供一种室温去除甲醛的耐湿催化剂,其由上述的钙钛矿结构材料制成。In a third aspect, the present invention provides a moisture-resistant catalyst for removing formaldehyde at room temperature, which is made of the above-mentioned perovskite structure material.
本发明的催化剂可以根据实际用途制备成型成不同的结构,例如用于空气净化装置中可以制成蜂窝状,用于密闭空间中摆放的可以制备成颗粒。The catalyst of the present invention can be prepared and molded into different structures according to actual uses. For example, it can be made into a honeycomb shape for use in an air purification device, and can be prepared into particles for placement in a closed space.
第四方面,本发明提供一种去除甲醛的方法,包括如下步骤:利用上述任一项所述的耐湿催化剂在室温下去除甲醛。In a fourth aspect, the present invention provides a method for removing formaldehyde, comprising the following steps: using any of the above-mentioned moisture-resistant catalysts to remove formaldehyde at room temperature.
所述耐湿催化剂可在室温环境湿度下的甲醛去除,将甲醛完全氧化为二氧化碳和水。The moisture-resistant catalyst can remove formaldehyde at room temperature and ambient humidity, completely oxidizing formaldehyde into carbon dioxide and water.
所述耐湿催化剂的除甲醛环境的湿度为0%~90%,优选为40%~65%。The humidity of the formaldehyde removal environment of the moisture-resistant catalyst is 0% to 90%, preferably 40% to 65%.
所述耐湿催化剂的除甲醛环境中甲醛的浓度为2~200ppm。The concentration of formaldehyde in the formaldehyde removal environment of the moisture-resistant catalyst is 2 to 200 ppm.
第五方面,本发明提供一种除甲醛装置,包括催化剂组件,所述催化剂组件中的催化剂为上述任一项所述的耐湿催化剂。In a fifth aspect, the present invention provides a formaldehyde removal device, comprising a catalyst assembly, wherein the catalyst in the catalyst assembly is the moisture-resistant catalyst described in any one of the above items.
所述除甲醛装置的组装过程如下:首先将粉末型的催化剂成型制备成催化剂单元,然后将催化剂单元进行组装形成去除甲醛的催化剂组件,其次将其放入空气净化装置中。The assembly process of the formaldehyde removal device is as follows: first, a powdered catalyst is molded into a catalyst unit, then the catalyst unit is assembled to form a catalyst assembly for removing formaldehyde, and then it is placed in an air purification device.
使用时,流动的空气从上述装置中通过,空气中含有的甲醛与装置中的催化剂组件接触,被催化剂氧化分解为二氧化碳和水,从而实现甲醛的去除。When in use, flowing air passes through the above device, and formaldehyde contained in the air contacts the catalyst component in the device and is oxidized and decomposed into carbon dioxide and water by the catalyst, thereby achieving the removal of formaldehyde.
与现有技术相比,本发明的优点是:Compared with the prior art, the advantages of the present invention are:
(1)本发明去除甲醛的耐湿钙钛矿晶型催化剂与贵金属催化剂相比成本低,制备方法简单。(1) Compared with precious metal catalysts, the moisture-resistant perovskite crystal catalyst for removing formaldehyde of the present invention has low cost and simple preparation method.
(2)本发明用于甲醛去除的催化剂的使用条件简单,操作实施方便,可用于室温下有效的去除甲醛污染,催化剂在室温环境湿度下能快速稳定的将甲醛完全氧化为CO2和H2O,不产生二次污染,CO2选择性达到100%,甲醛转化率可达到100%。(2) The catalyst for formaldehyde removal of the present invention has simple use conditions and is easy to operate and implement. It can be used to effectively remove formaldehyde pollution at room temperature. The catalyst can quickly and stably oxidize formaldehyde to CO2 and H2O completely at room temperature and humidity without generating secondary pollution. The CO2 selectivity reaches 100%, and the formaldehyde conversion rate can reach 100%.
(3)本发明催化剂在室温下去除甲醛,具有优异的耐湿性和稳定性。在相对湿度为40%和65%的条件下,甲醛转化率可达到100%,CO2选择性也达到100%。即使在相对湿度为90%的高湿度条件下,甲醛转化率能大于90%,CO2选择性达到100%,并且1000小时内,催化剂的甲醛转化率依然保持在90%。(3) The catalyst of the present invention removes formaldehyde at room temperature and has excellent moisture resistance and stability. Under conditions of relative humidity of 40% and 65%, the formaldehyde conversion rate can reach 100%, and the CO2 selectivity also reaches 100%. Even under high humidity conditions of 90% relative humidity, the formaldehyde conversion rate can be greater than 90%, the CO2 selectivity reaches 100%, and the formaldehyde conversion rate of the catalyst remains at 90% within 1000 hours.
附图说明BRIEF DESCRIPTION OF THE DRAWINGS
图1为本发明实施例1中制备得到的ZnMnO3的XRD图谱。FIG. 1 is an XRD pattern of ZnMnO 3 prepared in Example 1 of the present invention.
具体实施方式DETAILED DESCRIPTION
下面结合具体实施方式对本发明进行进一步的详细描述,给出的实施例仅为了阐明本发明,而不是为了限制本发明的范围。以下提供的实施例可作为本技术领域普通技术人员进行进一步改进的指南,并不以任何方式构成对本发明的限制。The present invention is further described in detail below in conjunction with specific embodiments, and the examples provided are only for illustrating the present invention, rather than for limiting the scope of the present invention. The examples provided below can be used as a guide for further improvements by those of ordinary skill in the art, and do not constitute a limitation of the present invention in any way.
下述实施例中的实验方法,如无特殊说明,均为常规方法,按照本领域内的文献所描述的技术或条件或者按照产品说明书进行。下述实施例中所用的材料、试剂等,如无特殊说明,均可从商业途径得到。The experimental methods in the following examples, unless otherwise specified, are all conventional methods, and are performed according to the techniques or conditions described in the literature in the field or according to the product instructions. The materials, reagents, etc. used in the following examples, unless otherwise specified, can all be obtained from commercial channels.
实施例1、制备室温去除甲醛的耐湿催化剂Example 1: Preparation of a moisture-resistant catalyst for removing formaldehyde at room temperature
按照如下步骤制备室温去除甲醛的耐湿催化剂:The moisture-resistant catalyst for removing formaldehyde at room temperature was prepared as follows:
(1)配制浓度为36mmol/L的碳酸氢铵溶液;将浓度为50mmol/L的硝酸锰溶液和浓度为50mmol/L的硝酸锌溶液按照体积比为1:1比例混合得到金属混合溶液锰锌溶液;(1) preparing an ammonium bicarbonate solution with a concentration of 36 mmol/L; mixing a manganese nitrate solution with a concentration of 50 mmol/L and a zinc nitrate solution with a concentration of 50 mmol/L in a volume ratio of 1:1 to obtain a metal mixed solution manganese zinc solution;
(2)将配置好的沉淀剂溶液碳酸氢铵溶液快速加入到金属混合溶液锰锌溶液中(沉淀剂溶液和金属混合溶液锰锌溶液的体积比为1:1),室温(25℃)搅拌12小时,用超纯水和无水乙醇洗涤产生的沉淀;(2) quickly adding the prepared precipitant solution ammonium bicarbonate solution to the metal mixed solution manganese zinc solution (the volume ratio of the precipitant solution to the metal mixed solution manganese zinc solution is 1:1), stirring at room temperature (25°C) for 12 hours, and washing the resulting precipitate with ultrapure water and anhydrous ethanol;
(3)将洗涤后的沉淀在60℃干燥6小时后于350℃空气中焙烧4小时,所得催化剂记为ZnMnO3。(3) The washed precipitate was dried at 60°C for 6 hours and then calcined in air at 350°C for 4 hours. The resulting catalyst was recorded as ZnMnO 3 .
ZnMnO3的XRD结果如图1所示,其为钙钛矿结构材料。The XRD result of ZnMnO 3 is shown in Figure 1, which is a perovskite structure material.
分别将0.2克催化剂ZnMnO3固定在石英的固定床反应器中,固定床反应器保持温度为25℃。反应气体组成为80ppm甲醛,氧气浓度为20%,氮气为平衡气体,气体流速是50mL/min。反应气体相对湿度分别为20%、40%、65%、90%,活性评价结果如表1。0.2 g of catalyst ZnMnO 3 was fixed in a quartz fixed bed reactor, and the fixed bed reactor was maintained at a temperature of 25°C. The reaction gas composition was 80 ppm formaldehyde, the oxygen concentration was 20%, nitrogen was the balance gas, and the gas flow rate was 50 mL/min. The relative humidity of the reaction gas was 20%, 40%, 65%, and 90%, respectively. The activity evaluation results are shown in Table 1.
表1、实施例1催化活性Table 1. Catalytic activity of Example 1
实施例2、制备室温去除甲醛的耐湿催化剂Example 2: Preparation of a moisture-resistant catalyst for removing formaldehyde at room temperature
按照如下步骤制备室温去除甲醛的耐湿催化剂:The moisture-resistant catalyst for removing formaldehyde at room temperature was prepared as follows:
(1)配制浓度为36mmol/L的碳酸氢铵溶液;将浓度为50mmol/L的硝酸锰溶液和浓度为50mmol/L的硝酸铁溶液按照体积比为1:1的比例混合得到金属混合溶液锰铁溶液;(1) preparing an ammonium bicarbonate solution with a concentration of 36 mmol/L; mixing a manganese nitrate solution with a concentration of 50 mmol/L and a ferric nitrate solution with a concentration of 50 mmol/L in a volume ratio of 1:1 to obtain a metal mixed solution, a manganese iron solution;
(2)将配置好的沉淀剂溶液碳酸氢铵溶液快速加入到金属混合溶液锰铁溶液中(沉淀剂溶液和金属混合溶液的体积比为1:1),室温(25℃)搅拌12小时,用超纯水和无水乙醇洗涤产生的沉淀;(2) quickly adding the prepared precipitant solution ammonium bicarbonate solution to the metal mixed solution manganese iron solution (the volume ratio of the precipitant solution to the metal mixed solution is 1:1), stirring at room temperature (25°C) for 12 hours, and washing the resulting precipitate with ultrapure water and anhydrous ethanol;
(3)将洗涤后的产电在60℃干燥6小时后于350℃空气中焙烧4小时,所得催化剂记为FeMnO3。(3) The washed electrocatalyst was dried at 60°C for 6 hours and then calcined in air at 350°C for 4 hours. The obtained catalyst was recorded as FeMnO 3 .
分别将0.2克催化剂FeMnO3固定在石英的固定床反应器中,固定床反应器保持温度为25℃。反应气体组成为160ppm甲醛,氧气浓度为20%,氮气为平衡气体,气体流速是50mL/min。反应气体相对湿度分别为20%、40%、65%、90%,活性评价结果如表2。0.2 g of catalyst FeMnO 3 was fixed in a quartz fixed bed reactor, and the fixed bed reactor was maintained at a temperature of 25°C. The reaction gas composition was 160 ppm formaldehyde, the oxygen concentration was 20%, nitrogen was the balance gas, and the gas flow rate was 50 mL/min. The relative humidity of the reaction gas was 20%, 40%, 65%, and 90%, respectively. The activity evaluation results are shown in Table 2.
表2、实施例2催化活性Table 2. Catalytic activity of Example 2
实施例3、制备室温去除甲醛的耐湿催化剂Example 3: Preparation of a moisture-resistant catalyst for removing formaldehyde at room temperature
按照如下步骤制备室温去除甲醛的耐湿催化剂:The moisture-resistant catalyst for removing formaldehyde at room temperature was prepared as follows:
(1)配制浓度为36mmol/L的碳酸氢铵溶液;将浓度为50mmol/L的硝酸锰溶液和浓度为50mmol/L的硝酸镍溶液按照体积比为1:1的比例混合得到金属混合溶液镍锰溶液;(1) preparing an ammonium bicarbonate solution with a concentration of 36 mmol/L; mixing a manganese nitrate solution with a concentration of 50 mmol/L and a nickel nitrate solution with a concentration of 50 mmol/L in a volume ratio of 1:1 to obtain a metal mixed solution of nickel-manganese solution;
(2)将配置好的沉淀剂溶液碳酸氢铵溶液快速加入到金属混合溶液锰镍溶液中(沉淀剂溶液和金属混合溶液的体积比为1:1),室温(25℃)搅拌12小时,用超纯水和无水乙醇洗涤产生的沉淀;(2) quickly adding the prepared precipitant solution ammonium bicarbonate solution to the metal mixed solution manganese nickel solution (the volume ratio of the precipitant solution to the metal mixed solution is 1:1), stirring at room temperature (25°C) for 12 hours, and washing the resulting precipitate with ultrapure water and anhydrous ethanol;
(3)将洗涤后的沉淀在60℃干燥6小时后于350℃空气中焙烧4小时,所得催化剂记为NiMnO3。(3) The washed precipitate was dried at 60°C for 6 hours and then calcined in air at 350°C for 4 hours. The obtained catalyst was recorded as NiMnO 3 .
分别将0.2克催化剂NiMnO3固定在石英的固定床反应器中,固定床反应器保持温度为25℃。反应气体组成为200ppm甲醛,氧气浓度为20%,氮气为平衡气体,气体流速是50mL/min。反应气体相对湿度分别为20%、40%、65%、90%,活性评价结果如表3。0.2 g of catalyst NiMnO 3 was fixed in a quartz fixed bed reactor, and the fixed bed reactor was maintained at a temperature of 25°C. The reaction gas composition was 200 ppm formaldehyde, the oxygen concentration was 20%, nitrogen was the balance gas, and the gas flow rate was 50 mL/min. The relative humidity of the reaction gas was 20%, 40%, 65%, and 90%, respectively. The activity evaluation results are shown in Table 3.
表3、实施例3催化活性Table 3, Catalytic activity of Example 3
实施例4Example 4
其余与实施例1一样,但催化剂用量为0.1克,甲醛初始浓度为20ppm。活性评价结果如表4。The rest is the same as in Example 1, except that the amount of catalyst used is 0.1 g and the initial formaldehyde concentration is 20 ppm. The activity evaluation results are shown in Table 4.
表4、实施例4催化活性Table 4, Catalytic activity of Example 4
实施例5Example 5
其余与实施例2一样,但催化剂用量为0.1克,甲醛初始浓度为8ppm。活性评价结果如表5。The rest is the same as Example 2, except that the amount of catalyst used is 0.1 g and the initial formaldehyde concentration is 8 ppm. The activity evaluation results are shown in Table 5.
表5、实施例5催化活性Table 5. Catalytic activity of Example 5
实施例6Example 6
其余与实施例3一样,但催化剂用量为0.1克,甲醛初始浓度为20ppm。活性评价结果如表6。The rest is the same as in Example 3, except that the amount of catalyst used is 0.1 g and the initial formaldehyde concentration is 20 ppm. The activity evaluation results are shown in Table 6.
表6、实施例6催化活性Table 6, Catalytic activity of Example 6
实施例7、制备室温去除甲醛的耐湿催化剂Example 7: Preparation of a moisture-resistant catalyst for removing formaldehyde at room temperature
按照如下步骤制备室温去除甲醛的耐湿催化剂:The moisture-resistant catalyst for removing formaldehyde at room temperature was prepared as follows:
(1)配制浓度为的36mmol/L碳酸氢铵溶液;将浓度为50mmol/L的硝酸锰溶液、浓度为25mmol/L的硝酸铁和浓度为25mmol/L的硝酸镍溶液按照体积比为1:1:1的比例混合得到金属混合溶液锰镍铁溶液;(1) preparing a 36 mmol/L ammonium bicarbonate solution; mixing a 50 mmol/L manganese nitrate solution, a 25 mmol/L iron nitrate solution, and a 25 mmol/L nickel nitrate solution in a volume ratio of 1:1:1 to obtain a metal mixed solution of manganese, nickel, and iron;
(2)将配置好的沉淀剂溶液碳酸氢铵溶液快速加入到金属混合溶液锰镍铁溶液中(沉淀剂溶液和金属混合溶液的体积比为1:1),室温(25℃)搅拌12小时,用超纯水和无水乙醇洗涤;(2) quickly adding the prepared precipitant solution ammonium bicarbonate solution to the metal mixed solution manganese nickel iron solution (the volume ratio of the precipitant solution to the metal mixed solution is 1:1), stirring at room temperature (25°C) for 12 hours, and washing with ultrapure water and anhydrous ethanol;
(3)将洗涤后的沉淀在60℃干燥6小时后于350℃空气中焙烧4小时,所得催化剂记为FexNi1-xMnO3(本实施例中x=0.5)。(3) The washed precipitate was dried at 60°C for 6 hours and then calcined in air at 350°C for 4 hours. The obtained catalyst was recorded as Fe x Ni 1-x MnO 3 (x=0.5 in this example).
分别将0.2克催化剂FexNi1-xMnO3固定在石英的固定床反应器中,固定床反应器保持温度为25℃。反应气体组成为2ppm甲醛,氧气浓度为20%,氮气为平衡气体,气体流速是50mL/min。反应气体相对湿度分别为20%、40%、65%、90%,活性评价结果如表7。0.2 g of catalyst Fe x Ni 1-x MnO 3 was fixed in a quartz fixed bed reactor, and the fixed bed reactor was maintained at a temperature of 25°C. The reaction gas composition was 2 ppm formaldehyde, the oxygen concentration was 20%, nitrogen was the balance gas, and the gas flow rate was 50 mL/min. The relative humidity of the reaction gas was 20%, 40%, 65%, and 90%, respectively. The activity evaluation results are shown in Table 7.
表7、实施例7催化活性Table 7, Catalytic activity of Example 7
实施例8Example 8
其余与实施例7一样,但甲醛初始浓度为180ppm。活性评价结果如表8。The rest is the same as Example 7, but the initial formaldehyde concentration is 180 ppm. The activity evaluation results are shown in Table 8.
表8、实施例8催化活性Table 8, Catalytic activity of Example 8
实施例9、制备室温去除甲醛的耐湿催化剂Example 9: Preparation of a moisture-resistant catalyst for removing formaldehyde at room temperature
按照如下步骤制备室温去除甲醛的耐湿催化剂:The moisture-resistant catalyst for removing formaldehyde at room temperature was prepared as follows:
(1)配制浓度为36mmol/L的碳酸氢铵溶液;将浓度为50mmol/L的硝酸锰溶液、浓度为25mmol/L的硝酸锌和浓度为25mmol/L的硝酸铁溶液按照体积比为1:1:1的比例混合得到金属混合溶液锰锌铁溶液;(1) preparing an ammonium bicarbonate solution with a concentration of 36 mmol/L; mixing a manganese nitrate solution with a concentration of 50 mmol/L, a zinc nitrate solution with a concentration of 25 mmol/L, and a ferric nitrate solution with a concentration of 25 mmol/L in a volume ratio of 1:1:1 to obtain a metal mixed solution of manganese, zinc, and iron;
(2)将配置好的沉淀剂溶液碳酸氢铵溶液快速加入到金属混合溶液锰锌铁溶液中(沉淀剂溶液和金属混合溶液的体积比为1:1),室温(25℃)搅拌12小时,用超纯水和无水乙醇洗涤;(2) quickly adding the prepared precipitant solution ammonium bicarbonate solution to the metal mixed solution manganese, zinc and iron solution (the volume ratio of the precipitant solution to the metal mixed solution is 1:1), stirring at room temperature (25°C) for 12 hours, and washing with ultrapure water and anhydrous ethanol;
(3)将洗涤后的沉淀在60℃干燥6小时后于350℃空气中焙烧4小时,所得催化剂记为ZnxFe1-xMnO3(本实施例中x=0.5)。(3) The washed precipitate was dried at 60°C for 6 hours and then calcined in air at 350°C for 4 hours. The obtained catalyst was recorded as ZnxFe1 -xMnO3 ( x=0.5 in this example).
分别将0.2克催化剂ZnxFe1-xMnO3固定在石英的固定床反应器中,固定床反应器保持温度为25℃。反应气体组成为60ppm甲醛,氧气浓度为20%,氮气为平衡气体,气体流速是50mL/min。反应气体相对湿度分别为20%、40%、65%、90%,活性评价结果如表9。0.2 g of catalyst Zn x Fe 1-x MnO 3 was fixed in a quartz fixed bed reactor, and the fixed bed reactor was maintained at a temperature of 25°C. The reaction gas composition was 60 ppm formaldehyde, the oxygen concentration was 20%, nitrogen was the balance gas, and the gas flow rate was 50 mL/min. The relative humidity of the reaction gas was 20%, 40%, 65%, and 90%, respectively. The activity evaluation results are shown in Table 9.
表9、实施例9催化活性Table 9, Catalytic activity of Example 9
实施例10Example 10
其余与实施例9一样,但甲醛初始浓度为200ppm。活性评价结果如表10。The rest is the same as Example 9, but the initial concentration of formaldehyde is 200 ppm. The activity evaluation results are shown in Table 10.
表10、实施例10催化活性Table 10, Catalytic Activity of Example 10
实施例11、制备室温去除甲醛的耐湿催化剂Example 11: Preparation of a moisture-resistant catalyst for removing formaldehyde at room temperature
按照如下步骤制备室温去除甲醛的耐湿催化剂:The moisture-resistant catalyst for removing formaldehyde at room temperature was prepared as follows:
(1)配制浓度为36mmol/L的碳酸氢铵溶液;将浓度为50mmol/L的硝酸锰溶液、浓度为25mmol/L的硝酸锌和浓度为25mmol/L的硝酸镍溶液按照体积比为1:1:1的比例混合得到金属混合溶液锰锌镍溶液;(1) preparing an ammonium bicarbonate solution with a concentration of 36 mmol/L; mixing a manganese nitrate solution with a concentration of 50 mmol/L, a zinc nitrate solution with a concentration of 25 mmol/L, and a nickel nitrate solution with a concentration of 25 mmol/L in a volume ratio of 1:1:1 to obtain a metal mixed solution of manganese, zinc, and nickel;
(2)将配置好的沉淀剂溶液碳酸氢铵溶液快速加入到金属混合溶液锰锌镍溶液中(沉淀剂溶液和金属混合溶液的体积比为1:1),室温(25℃)搅拌12小时,用超纯水和无水乙醇洗涤;(2) quickly adding the prepared precipitant solution ammonium bicarbonate solution to the metal mixed solution manganese zinc nickel solution (the volume ratio of the precipitant solution to the metal mixed solution is 1:1), stirring at room temperature (25°C) for 12 hours, and washing with ultrapure water and anhydrous ethanol;
(3)将洗涤后的沉淀在60℃干燥6小时后于350℃空气中焙烧4小时,所得催化剂记为ZnxNi1-xMnO3(本实施例中x=0.5)。(3) The washed precipitate was dried at 60°C for 6 hours and then calcined in air at 350°C for 4 hours. The obtained catalyst was recorded as ZnxNi1 -xMnO3 ( x=0.5 in this example).
分别将0.2克催化剂ZnxNi1-xMnO3固定在石英的固定床反应器中,固定床反应器保持温度为25℃。反应气体组成为20ppm甲醛,氧气浓度为20%,氮气为平衡气体,气体流速是50mL/min。反应气体相对湿度分别为20%、40%、65%、90%,活性评价结果如表11。0.2 g of catalyst Zn x Ni 1-x MnO 3 was fixed in a quartz fixed bed reactor, and the fixed bed reactor was maintained at a temperature of 25°C. The reaction gas composition was 20 ppm formaldehyde, the oxygen concentration was 20%, nitrogen was the balance gas, and the gas flow rate was 50 mL/min. The relative humidity of the reaction gas was 20%, 40%, 65%, and 90%, respectively. The activity evaluation results are shown in Table 11.
表11、实施例11催化活性Table 11, Catalytic activity of Example 11
实施例12Example 12
其余与实施例11一样,但甲醛初始浓度为200ppm。活性评价结果如表12。The rest is the same as Example 11, but the initial formaldehyde concentration is 200 ppm. The activity evaluation results are shown in Table 12.
表12、实施例12催化活性Table 12, Catalytic activity of Example 12
实施例13Example 13
分别将0.2克实施例1催化剂ZnMnO3放在含有甲醛的密闭的10L透明仓,反应温度为25℃。甲醛气体由聚甲醛挥发生成,浓度为10ppm,空气中氧气浓度约为20%,反应气体相对湿度分别为20%、40%、65%、90%。反应60分种后,甲醛检测器检测甲醛浓度均降为0ppm。0.2 g of the catalyst ZnMnO 3 of Example 1 was placed in a sealed 10 L transparent chamber containing formaldehyde at a reaction temperature of 25°C. Formaldehyde gas was generated by the volatilization of polyoxymethylene with a concentration of 10 ppm. The oxygen concentration in the air was about 20%. The relative humidity of the reaction gas was 20%, 40%, 65%, and 90%, respectively. After 60 minutes of reaction, the formaldehyde concentration detected by the formaldehyde detector dropped to 0 ppm.
实施例14Embodiment 14
其余与实施例13一样,但甲醛初始浓度为120ppm。活性评价结果如表13。The rest is the same as Example 13, but the initial formaldehyde concentration is 120 ppm. The activity evaluation results are shown in Table 13.
表13、实施例14催化活性Table 13, Catalytic activity of Example 14
实施例15Embodiment 15
其余与实施例13一样,但甲醛初始浓度为200ppm。活性评价结果如表14。The rest is the same as Example 13, but the initial formaldehyde concentration is 200 ppm. The activity evaluation results are shown in Table 14.
表14、实施例15催化活性Table 14, Catalytic activity of Example 15
实施例16Example 16
分别将0.2克实施例2催化剂FeMnO3放在含有甲醛的密闭的10L透明仓,反应温度为25℃。甲醛气体由聚甲醛挥发生成,浓度为80ppm,空气中氧气浓度约为20%,反应气体相对湿度分别为20%、40%、65%、90%。反应60分种后,甲醛检测器检测甲醛浓度,活性评价结果如表15。0.2 g of the catalyst FeMnO 3 of Example 2 was placed in a sealed 10 L transparent chamber containing formaldehyde, and the reaction temperature was 25°C. Formaldehyde gas was generated by the volatilization of polyoxymethylene, with a concentration of 80 ppm. The oxygen concentration in the air was about 20%, and the relative humidity of the reaction gas was 20%, 40%, 65%, and 90%, respectively. After 60 minutes of reaction, the formaldehyde concentration was detected by a formaldehyde detector, and the activity evaluation results are shown in Table 15.
表15、实施例16催化活性Table 15, Catalytic activity of Example 16
实施例17Embodiment 17
其余与实施例16一样,但甲醛初始浓度为200ppm。活性评价结果如表16。The rest is the same as Example 16, but the initial formaldehyde concentration is 200 ppm. The activity evaluation results are shown in Table 16.
表16、实施例17催化活性Table 16, Catalytic Activity of Example 17
实施例18Embodiment 18
分别将0.2克实施例3催化剂NiMnO3放在含有甲醛的密闭的10L透明仓,反应温度为25℃。甲醛气体由聚甲醛挥发生成,浓度为2ppm,空气中氧气浓度约为20%,反应气体相对湿度分别为20%、40%、65%、90%。反应60分种后,甲醛检测器检测甲醛浓度均降为0ppm。0.2 g of the catalyst NiMnO 3 of Example 3 was placed in a sealed 10 L transparent chamber containing formaldehyde, and the reaction temperature was 25°C. Formaldehyde gas was generated by the volatilization of polyoxymethylene, with a concentration of 2 ppm. The oxygen concentration in the air was about 20%, and the relative humidity of the reaction gas was 20%, 40%, 65%, and 90%, respectively. After 60 minutes of reaction, the formaldehyde concentration detected by the formaldehyde detector dropped to 0 ppm.
实施例19Embodiment 19
其余与实施例18一样,但甲醛浓度为200ppm。活性评价结果如表17。The rest was the same as in Example 18, except that the formaldehyde concentration was 200 ppm. The activity evaluation results are shown in Table 17.
表17、实施例19催化活性Table 17, Catalytic Activity of Example 19
实施例20
分别将0.1克实施例11催化剂ZnxNi1-xMnO3放在含有甲醛的密闭的10L透明仓,反应温度为25℃。甲醛气体由聚甲醛挥发生成,浓度为2ppm,空气中氧气浓度约为20%,反应气体相对湿度分别为20%、40%、65%、90%。反应60分种后,甲醛检测器检测甲醛浓度均降为0ppm。0.1 g of the catalyst Zn x Ni 1-x MnO 3 of Example 11 was placed in a sealed 10 L transparent chamber containing formaldehyde at a reaction temperature of 25°C. Formaldehyde gas was generated by the volatilization of polyoxymethylene with a concentration of 2 ppm. The oxygen concentration in the air was about 20%. The relative humidity of the reaction gas was 20%, 40%, 65%, and 90%, respectively. After 60 minutes of reaction, the formaldehyde concentration detected by the formaldehyde detector dropped to 0 ppm.
实施例21Embodiment 21
其余与实施例20一样,但甲醛浓度为180ppm。活性评价结果如表18。The rest was the same as in Example 20, except that the formaldehyde concentration was 180 ppm. The activity evaluation results are shown in Table 18.
表18、实施例21催化活性Table 18, Catalytic Activity of Example 21
实施例22Example 22
分别将0.1克实施例7催化剂FexNi1-xMnO3放在含有甲醛的密闭的10L透明仓中,反应温度为25℃。甲醛气体由聚甲醛挥发生成,浓度为5ppm,空气中氧气浓度约为20%,反应气体相对湿度分别为20%、40%、65%、90%。反应60分种后,甲醛检测器检测甲醛浓度均降为0ppm。0.1 g of the catalyst Fe x Ni 1-x MnO 3 of Example 7 was placed in a sealed 10 L transparent chamber containing formaldehyde, and the reaction temperature was 25°C. Formaldehyde gas was generated by the volatilization of polyoxymethylene, with a concentration of 5 ppm. The oxygen concentration in the air was about 20%, and the relative humidity of the reaction gas was 20%, 40%, 65%, and 90%, respectively. After 60 minutes of reaction, the formaldehyde concentration detected by the formaldehyde detector dropped to 0 ppm.
实施例23Embodiment 23
其余与实施例22一样,但甲醛初始浓度为200ppm。活性评价结果如表19。The rest is the same as Example 22, but the initial formaldehyde concentration is 200 ppm. The activity evaluation results are shown in Table 19.
表19、实施例23催化活性Table 19, Catalytic Activity of Example 23
实施例24、Embodiment 24,
首先分别将500克粉末型的FexNi1-xMnO3催化剂成型制备成颗粒状催化剂单元(颗粒大小为0.5-1cm长,直径0.1-0.5的圆柱体颗粒),然后将颗粒状催化剂单元装入多孔盒子里制成去除甲醛的催化剂组件,随后将其放入空气净化装置的换风口处,最后将空气净化装置放于20m2的大气仓中。大气仓温度为25℃。甲醛气体由聚甲醛挥发产生,浓度为2ppm,空气中氧气浓度约为20%,反应气体相对湿度分别为20%、40%、65%、90%。反应60分钟后,甲醛浓度均降为0ppm。First, 500 grams of powdered Fe x Ni 1-x MnO 3 catalyst were molded into granular catalyst units (cylindrical particles with a particle size of 0.5-1 cm long and 0.1-0.5 in diameter), and then the granular catalyst units were placed in a porous box to make a catalyst assembly for removing formaldehyde, which was then placed in the air exchange port of an air purification device, and finally the air purification device was placed in a 20m 2 atmospheric chamber. The atmospheric chamber temperature was 25°C. Formaldehyde gas was generated by the volatilization of polyoxymethylene with a concentration of 2ppm, the oxygen concentration in the air was about 20%, and the relative humidity of the reaction gas was 20%, 40%, 65%, and 90%, respectively. After 60 minutes of reaction, the formaldehyde concentration dropped to 0ppm.
以上实施例仅为本发明的具体实例方式展示,用来说明本发明中催化剂的详细组成及其用途,但不代表本发明仅依赖上述详细的组成及用途才能实施。因此,本发明的保护范围不局限于以上实施例,凡是对本发明中催化剂原料的替换或优化比例,添加其他辅助成分、用途参数的优化或替换等,均在本发明的保护范围内。The above embodiments are only specific examples of the present invention, which are used to illustrate the detailed composition and use of the catalyst in the present invention, but do not mean that the present invention can only be implemented by relying on the above detailed composition and use. Therefore, the protection scope of the present invention is not limited to the above embodiments, and any replacement or optimization ratio of the catalyst raw materials in the present invention, addition of other auxiliary components, optimization or replacement of application parameters, etc., are all within the protection scope of the present invention.
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