CN116809111A - A catalyst and catalytic converter for zero emission of N2O in gasoline engines - Google Patents
A catalyst and catalytic converter for zero emission of N2O in gasoline engines Download PDFInfo
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Abstract
Description
技术领域Technical field
本申请涉及汽油机尾气处理技术领域,特别是涉及一种汽油机N2O零排放的催化剂及催化器。This application relates to the technical field of gasoline engine exhaust gas treatment, and in particular to a catalyst and catalytic converter for zero emission of N 2 O in gasoline engines.
背景技术Background technique
N2O是一种无色有甜味的气体,有麻醉作用。N2O为痕量气体,对温室效应的贡献是CH4的21倍,N2O全球增暖潜能(GWP,Global warming potential)是CO2的310倍。N2O的大气浓度每增加1倍就将导致全球升温0.3℃。N2O很稳定,停留时间长达120年。因此,由N2O排放造成的大气环境破坏是十分严重的。N 2 O is a colorless, sweet gas that has anesthetic effects. N 2 O is a trace gas, and its contribution to the greenhouse effect is 21 times that of CH 4. The global warming potential (GWP) of N 2 O is 310 times that of CO 2 . Every doubling of the atmospheric concentration of N 2 O will cause global warming to rise by 0.3°C. N 2 O is very stable and has a residence time of up to 120 years. Therefore, the damage to the atmospheric environment caused by N 2 O emissions is very serious.
大气中N2O主要来自农业、工业和化石燃料燃烧、生物质燃烧、废水及城市垃圾等,其中农业N2O排放量占全球N2O排放量的比例超过2/3。全球运输的排放量占目前人为排放总量估计值的3±1%。国内机动车温室气体排放状况的研究也表明,轻型客车、汽油车是机动车N2O排放的主要来源。N 2 O in the atmosphere mainly comes from agriculture, industry, fossil fuel combustion, biomass burning, wastewater and urban garbage, among which agricultural N 2 O emissions account for more than 2/3 of global N 2 O emissions. Global transport emissions account for 3±1% of current estimates of total anthropogenic emissions. Research on greenhouse gas emissions from domestic motor vehicles also shows that light passenger vehicles and gasoline vehicles are the main sources of N 2 O emissions from motor vehicles.
由于N2O的活性不高,与大气中已知的绝大多数气体难以发生反应,使N2O的处理变得非常困难,N2O的活化、激活和分裂是一项研究与工程应用的挑战性的工作。目前,汽油机尾气中的N2O尚得不到有效的处理Since N 2 O is not highly active, it is difficult to react with most known gases in the atmosphere, making the treatment of N 2 O very difficult. The activation, activation and splitting of N 2 O is a research and engineering application. challenging work. At present, N 2 O in gasoline engine exhaust has not been effectively treated
发明内容Contents of the invention
针对现有技术中车用汽油机三元催化器不能使N2O达到零排放的问题,本发明提出一种汽油机N2O零排放的催化剂及催化器,使汽油机三元催化器后的N2O排放实现零排放目标。In view of the problem in the prior art that the three-way catalytic converter for automobile gasoline engines cannot achieve zero emission of N 2 O, the present invention proposes a catalyst and catalytic converter for zero emission of N 2 O in gasoline engines, which can reduce the N 2 O emission after the three-way catalytic converter of the gasoline engine. Achieve zero emission goals.
本发明提供的一种汽油机N2O零排放的催化剂,所述催化剂以Rh为主催化剂、CeO2为助催化剂,以石墨烯对分子筛改性后的石墨烯/分子筛作为多层级结构的涂层、蜂窝状堇青石陶瓷为载体。The invention provides a catalyst for zero emission of N 2 O in gasoline engines. The catalyst uses Rh as the main catalyst, CeO 2 as the cocatalyst, and graphene/molecular sieve modified by graphene as a multi-layered structure coating. , honeycomb cordierite ceramic as carrier.
优选地,在堇青石载体上的涂层顺序依次为石墨烯/分子筛/石墨烯的多层级结构,通道表面层为石墨烯。Preferably, the coating sequence on the cordierite carrier is a multi-level structure of graphene/molecular sieve/graphene, and the channel surface layer is graphene.
优选地,在堇青石载体上的涂层顺序依次为分子筛/石墨烯/分子筛等的多层级结构,通道表面层为分子筛。Preferably, the coating sequence on the cordierite carrier is a multi-level structure of molecular sieve/graphene/molecular sieve, etc., and the channel surface layer is molecular sieve.
优选地,将堇青石载体沿通道方向分为前后两部分,前半部分的涂层顺序依次为石墨烯/分子筛/石墨烯等的多层级结构,通道表面层为石墨烯;后半部分的涂层顺序依次为分子筛/石墨烯/分子筛等的多层级结构,通道表面层为分子筛。Preferably, the cordierite carrier is divided into two parts, front and rear, along the channel direction. The coating sequence of the first half is a multi-level structure of graphene/molecular sieve/graphene, etc., and the channel surface layer is graphene; the coating of the second half is The sequence is a multi-level structure of molecular sieve/graphene/molecular sieve, etc., and the channel surface layer is molecular sieve.
优选地,将堇青石载体沿通道方向分为前后两部分,前半部分的涂层顺序依次为分子筛/石墨烯/分子筛等的多层级结构,通道表面层为分子筛;后半部分的涂层顺序依次为石墨烯/分子筛/石墨烯等的多层级结构,通道表面层为石墨烯。Preferably, the cordierite carrier is divided into two parts, front and rear, along the channel direction. The coating sequence of the first half is a multi-level structure of molecular sieve/graphene/molecular sieve, etc., and the channel surface layer is molecular sieve; the coating sequence of the second half is sequentially. It is a multi-level structure of graphene/molecular sieve/graphene, etc., and the channel surface layer is graphene.
进一步地,所述Rh催化剂、CeO2助催化剂直接涂敷在石墨烯或分子筛通道表面上。Further, the Rh catalyst and CeO 2 cocatalyst are directly coated on the graphene or molecular sieve channel surface.
优选地,所述Rh催化剂、CeO2助催化剂还涂敷在结构内部的石墨烯或分子筛表面。Preferably, the Rh catalyst and CeO 2 cocatalyst are also coated on the surface of graphene or molecular sieve inside the structure.
本发明还提供了上述催化剂的制备方法,包括如下步骤:The invention also provides a preparation method for the above catalyst, which includes the following steps:
石墨烯对分子筛改性方法如下:The method for modifying molecular sieves with graphene is as follows:
1)利用原位水热合成法,将蜂窝状堇青石陶瓷载体置于配置好的分子筛前驱体溶液中,进行原位晶化,使分子筛直接“生长”在载体上,获得分子筛涂层。1) Using the in-situ hydrothermal synthesis method, the honeycomb cordierite ceramic carrier is placed in the configured molecular sieve precursor solution, and in-situ crystallization is performed, so that the molecular sieve is directly "grown" on the carrier to obtain a molecular sieve coating.
2)直接在氧化石墨烯水溶液中加入水合肼,再用水热法还原制备石墨烯溶液,制得了在水中均匀、稳定分散的石墨烯溶液;2) Directly add hydrazine hydrate to the graphene oxide aqueous solution, and then reduce it by hydrothermal method to prepare the graphene solution, and obtain a graphene solution that is evenly and stably dispersed in water;
3)将具有分子筛涂层的蜂窝状堇青石陶瓷载体置于石墨烯溶液中,利用超声浸渍法,将石墨烯高度分散至分子筛表面、孔道之中,完成对分子筛的表面、孔道改性,获得石墨烯对分子筛改性后的石墨烯/分子筛涂层。3) Place the honeycomb cordierite ceramic carrier with molecular sieve coating in the graphene solution, and use the ultrasonic impregnation method to highly disperse the graphene into the surface and pores of the molecular sieve to complete the modification of the surface and pores of the molecular sieve to obtain Graphene/molecular sieve coating after graphene modification of molecular sieve.
4)进一步,重复上述步骤,可获得多层级结构的涂层。4) Further, repeat the above steps to obtain a multi-layered coating.
本发明还提供了一种汽油机N2O零排放的催化器,由上述的催化剂封装而成。The invention also provides a gasoline engine N 2 O zero-emission catalytic converter, which is packaged by the above-mentioned catalyst.
相较于现有技术,本发明的技术方案具有如下优点:Compared with the existing technology, the technical solution of the present invention has the following advantages:
(1)石墨烯/分子筛的多层级交错结构使催化剂与N2O的接触面积显著增加,可增加N2O的吸附量。(1) The multi-level staggered structure of graphene/molecular sieve significantly increases the contact area between the catalyst and N2O, which can increase the adsorption amount of N2O .
(2)石墨烯/分子筛的多层级交错结构使催化剂的内部纳米孔结构空间显著增加,可增加N2O在纳米孔中的分子扩散行程,延长N2O的吸附与扩散时间。(2) The multi-level staggered structure of graphene/molecular sieve significantly increases the internal nanopore structure space of the catalyst, which can increase the molecular diffusion path of N 2 O in the nanopores and prolong the adsorption and diffusion time of N 2 O.
(3)石墨烯/分子筛的多层级交错结构可提高催化器的导热性能和热扩散性能,快速提高发动机低温起动工况下的N2O催化器内部温度,使催化器有充足的起燃时间。(3) The multi-level staggered structure of graphene/molecular sieve can improve the thermal conductivity and thermal diffusion performance of the catalytic converter, quickly increase the internal temperature of the N 2 O catalytic converter under low-temperature starting conditions of the engine, and allow the catalytic converter to have sufficient ignition time. .
(4)小孔结构分子筛具有晶体结构,可保证分子筛的热稳定性和结构稳定性。石墨烯对分子筛的改性,可进一步保证分子筛的热稳定性、水热稳定性,满足汽油机的工况要求。(4) The small pore structure molecular sieve has a crystal structure, which can ensure the thermal stability and structural stability of the molecular sieve. The modification of molecular sieves by graphene can further ensure the thermal and hydrothermal stability of the molecular sieves and meet the working conditions of gasoline engines.
(5)根据N2O的结构与极性开展石墨烯对分子筛孔道结构与吸附性能的调控,实现对N2O的择形吸附与催化,达到对N2O的零排放目标。(5) According to the structure and polarity of N 2 O, graphene can regulate the pore structure and adsorption performance of molecular sieves to achieve shape-selective adsorption and catalysis of N 2 O and achieve the goal of zero emission of N 2 O.
附图说明Description of the drawings
为了更清楚地说明本申请实施例或现有技术中的技术方案,下面将对实施例或现有技术描述中所需要使用的附图作简单地介绍,显而易见地,下面描述中的附图仅仅是本申请的一些实施例,对于本领域普通技术人员来讲,在不付出创造性劳动的前提下,还可以根据这些附图获得其他的附图。In order to explain the embodiments of the present application or the technical solutions in the prior art more clearly, the drawings needed to be used in the description of the embodiments or the prior art will be briefly introduced below. Obviously, the drawings in the following description are only These are some embodiments of the present application. For those of ordinary skill in the art, other drawings can be obtained based on these drawings without exerting creative efforts.
图1为本发明中汽油机N2O零排放催化剂的结构示意图;Figure 1 is a schematic structural diagram of the N 2 O zero emission catalyst of the gasoline engine in the present invention;
图2为本发明中汽油机N2O零排放催化剂中不同多层级涂层的结构示意图;Figure 2 is a schematic structural diagram of different multi-layer coatings in the N 2 O zero emission catalyst of the gasoline engine of the present invention;
其中,(a)表示在堇青石载体上的涂层顺序依次为石墨烯/分子筛/石墨烯等的多层级结构,通道表面层为石墨烯;(b)表示在堇青石载体上的涂层顺序依次为分子筛/石墨烯/分子筛等的多层级结构,通道表面层为分子筛;(c)表示将堇青石载体沿通道方向分为前后两部分,前半部分的涂层顺序依次为石墨烯/分子筛/石墨烯等的多层级结构,通道表面层为石墨烯;后半部分的涂层顺序依次为分子筛/石墨烯/分子筛等的多层级结构,通道表面层为分子筛;(d)表示将堇青石载体沿通道方向分为前后两部分,前半部分的涂层顺序依次为分子筛/石墨烯/分子筛等的多层级结构,通道表面层为分子筛;后半部分的涂层顺序依次为石墨烯/分子筛/石墨烯等的多层级结构,通道表面层为石墨烯。Among them, (a) represents the coating sequence on the cordierite carrier, which is a multi-level structure of graphene/molecular sieve/graphene, etc., and the channel surface layer is graphene; (b) represents the coating sequence on the cordierite carrier. The order is a multi-level structure of molecular sieve/graphene/molecular sieve, etc., and the channel surface layer is molecular sieve; (c) indicates that the cordierite carrier is divided into front and rear parts along the channel direction, and the coating order of the first half is graphene/molecular sieve/ The multi-level structure of graphene, etc., the channel surface layer is graphene; the coating sequence of the second half is a multi-level structure of molecular sieve/graphene/molecular sieve, etc., the channel surface layer is molecular sieve; (d) represents the cordierite carrier It is divided into two parts along the channel direction. The coating order of the first half is a multi-level structure of molecular sieve/graphene/molecular sieve, etc., and the surface layer of the channel is molecular sieve. The coating order of the second half is graphene/molecular sieve/graphite. It has a multi-level structure such as graphene, and the channel surface layer is graphene.
图3为本发明中汽油机N2O零排放催化剂中不同催化剂涂覆位置的结构示意图;Figure 3 is a schematic structural diagram of different catalyst coating positions in the N 2 O zero emission catalyst of the gasoline engine of the present invention;
其中,(a)表示Rh催化剂、CeO2助催化剂直接涂敷在石墨烯或分子筛通道表面上;(b)表示Rh催化剂、CeO2助催化剂按照分子筛/石墨烯改性的多层级交错结构,分别涂敷在分子筛/石墨烯表面上Among them, (a) indicates that the Rh catalyst and CeO 2 cocatalyst are directly coated on the surface of graphene or molecular sieve channels; (b) indicates that the Rh catalyst and CeO 2 cocatalyst are modified according to the multi-level staggered structure of molecular sieve/graphene, respectively. Coated on molecular sieve/graphene surface
图4为汽油机尾气中的一些分子极性示意图;Figure 4 is a schematic diagram of the polarity of some molecules in gasoline engine exhaust;
图5为本发明中的N2O零排放催化剂中石墨烯/分子筛对N2O择形吸附与催化示意图;Figure 5 is a schematic diagram of N 2 O shape-selective adsorption and catalysis by graphene/molecular sieve in the N 2 O zero emission catalyst of the present invention;
图6为本发明中的汽油机N2O零排放催化器在汽油机排气后处理系统中的结构示意图;Figure 6 is a schematic structural diagram of the gasoline engine N 2 O zero emission catalytic converter in the gasoline engine exhaust after-treatment system in the present invention;
图7为本发明中汽油机N2O催化器的结构示意图;Figure 7 is a schematic structural diagram of the N 2 O catalytic converter of the gasoline engine in the present invention;
其中,(a)表示N2O催化器;(b)表示催化器内部蜂窝状结构的径向剖视图;(c)表示中间局部轴向通道剖视图;(d)表示边界局部轴向通道剖视图;(e)表示通道局部表面结构图;Among them, (a) represents the N 2 O catalytic converter; (b) represents the radial sectional view of the honeycomb structure inside the catalytic converter; (c) represents the sectional view of the partial axial channel in the middle; (d) represents the sectional view of the partial axial channel at the boundary; ( e) represents the local surface structure diagram of the channel;
图8为汽油机N2O零排放催化剂中的N2O物理、化学吸附过程示意图;Figure 8 is a schematic diagram of the physical and chemical adsorption process of N 2 O in the N 2 O zero-emission catalyst of a gasoline engine;
其中,(a)表示物理吸附,(b)表示化学吸附Among them, (a) represents physical adsorption, (b) represents chemical adsorption
具体实施方式Detailed ways
为使本申请的上述目的、特征和优点能够更加明显易懂,下面结合附图对本申请的具体实施方式做详细的说明。在下面的描述中阐述了很多具体细节以便于充分理解本申请。但是本申请能够以很多不同于在此描述的其它方式来实施,本领域技术人员可以在不违背本申请内涵的情况下做类似改进,因此本申请不受下面公开的具体实施例的限制。In order to make the above objects, features and advantages of the present application more obvious and easy to understand, the specific implementation modes of the present application will be described in detail below with reference to the accompanying drawings. In the following description, numerous specific details are set forth in order to provide a thorough understanding of the present application. However, the present application can be implemented in many other ways different from those described here. Those skilled in the art can make similar improvements without violating the connotation of the present application. Therefore, the present application is not limited by the specific embodiments disclosed below.
一种汽油机N2O零排放的催化剂,如图1所示,所述催化剂以Rh为主催化剂、CeO2为助催化剂,以石墨烯对分子筛改性后的石墨烯/分子筛作为多层级结构的涂层、蜂窝状堇青石陶瓷为载体。多层结构如图2-3所示。A catalyst for zero emission of N 2 O in gasoline engines, as shown in Figure 1. The catalyst uses Rh as the main catalyst, CeO 2 as the cocatalyst, and uses graphene/molecular sieve modified by graphene as a multi-level structure. Coating, honeycomb cordierite ceramic as carrier. The multi-layer structure is shown in Figure 2-3.
在较为优选的具体实施方式中,如图2(a)所示,在堇青石载体上的涂层顺序依次为石墨烯/分子筛/石墨烯的多层级结构,通道表面层为石墨烯。In a preferred embodiment, as shown in Figure 2(a), the coating sequence on the cordierite carrier is a multi-level structure of graphene/molecular sieve/graphene, and the channel surface layer is graphene.
在较为优选的具体实施方式中,如图2(b)所示,在堇青石载体上的涂层顺序依次为分子筛/石墨烯/分子筛等的多层级结构,通道表面层为分子筛。In a preferred embodiment, as shown in Figure 2(b), the coating sequence on the cordierite carrier is a multi-level structure of molecular sieve/graphene/molecular sieve, etc., and the channel surface layer is molecular sieve.
在较为优选的具体实施方式中,如图2(c)所示,将堇青石载体沿通道方向分为前后两部分,前半部分的涂层顺序依次为石墨烯/分子筛/石墨烯等的多层级结构,通道表面层为石墨烯;后半部分的涂层顺序依次为分子筛/石墨烯/分子筛等的多层级结构,通道表面层为分子筛。In a more preferred embodiment, as shown in Figure 2(c), the cordierite carrier is divided into two parts, the front and back parts along the channel direction, and the coating sequence of the first half is multi-layered graphene/molecular sieve/graphene, etc. Structure, the channel surface layer is graphene; the coating sequence of the second half is a multi-level structure of molecular sieve/graphene/molecular sieve, etc., and the channel surface layer is molecular sieve.
在较为优选的具体实施方式中,如图2(d)所示,将堇青石载体沿通道方向分为前后两部分,前半部分的涂层顺序依次为分子筛/石墨烯/分子筛等的多层级结构,通道表面层为分子筛;后半部分的涂层顺序依次为石墨烯/分子筛/石墨烯等的多层级结构,通道表面层为石墨烯。In a preferred embodiment, as shown in Figure 2(d), the cordierite carrier is divided into front and rear parts along the channel direction, and the coating sequence of the first half is a multi-level structure of molecular sieve/graphene/molecular sieve, etc. , the channel surface layer is molecular sieve; the coating sequence of the second half is a multi-level structure of graphene/molecular sieve/graphene, etc., and the channel surface layer is graphene.
在上述结构的基础上,提出Rh催化剂、CeO2助催化剂的多层级交错结构方案或与其类似方案。可以采取通道表面的单层涂敷,即Rh催化剂、CeO2助催化剂直接涂敷在石墨烯或分子筛通道表面上。如图3(a)所示,即所述Rh催化剂、CeO2助催化剂直接涂敷在石墨烯或分子筛通道表面上。On the basis of the above structure, a multi-level staggered structure scheme of Rh catalyst, CeO 2 cocatalyst or similar scheme is proposed. Single-layer coating on the channel surface can be adopted, that is, Rh catalyst and CeO 2 cocatalyst are directly coated on the graphene or molecular sieve channel surface. As shown in Figure 3(a), the Rh catalyst and CeO 2 cocatalyst are directly coated on the surface of graphene or molecular sieve channels.
如图3(b)所示,Rh催化剂、CeO2助催化剂在结构内部与通道表面的多层级交错涂敷,即所述Rh催化剂、CeO2助催化剂还涂敷在结构内部的石墨烯或分子筛表面。通道表面的单层涂敷与现有三元催化器的结构类似,而结构内部与通道表面的多层级交错涂敷可进一步提高吸附器的储氧、释氧能力,有利于对氧分子的调控。多层涂敷的Rh主催化剂、CeO2助催化剂的结构可增大催化剂与N2O的接触面积及孔内结构空间扩散区域,延长N2O的吸附时间,提高发动机低温起动工况下的N2O催化剂内部温度。As shown in Figure 3(b), the Rh catalyst and CeO 2 co-catalyst are coated in multiple layers inside the structure and on the surface of the channel, that is, the Rh catalyst and CeO 2 co-catalyst are also coated on the graphene or molecular sieve inside the structure. surface. The single-layer coating on the channel surface is similar to the structure of the existing three-way catalytic converter, while the multi-level staggered coating inside the structure and on the channel surface can further improve the oxygen storage and release capacity of the adsorber, which is beneficial to the control of oxygen molecules. The structure of the multi-layer coated Rh main catalyst and CeO 2 cocatalyst can increase the contact area between the catalyst and N 2 O and the spatial diffusion area of the structure in the pores, prolong the adsorption time of N 2 O, and improve the performance of the engine under low temperature starting conditions. N 2 O catalyst internal temperature.
如图4所示,排气成分中,N2O是直线型的极性分子;CO2是直线形的非极性分子;H2O的分子结构是V形结构的极性分子;NH3的空间结构是三角锥型的极性分子。根据N2O分子的结构与极性,利用石墨烯的孔结构可调控性,对分子筛孔结构进行调控,改变其结构与比表面积,使其孔的大小与极性适合N2O分子的吸附与扩散。改性后的石墨烯/分子筛对N2O择形吸附与催化,同时减少H2O、NH3的影响,如图5所示。As shown in Figure 4, among the exhaust components, N 2 O is a linear polar molecule; CO 2 is a linear non-polar molecule; the molecular structure of H 2 O is a V-shaped polar molecule; NH 3 The spatial structure is a triangular pyramidal polar molecule. According to the structure and polarity of N 2 O molecules, the pore structure of graphene can be adjusted to adjust the pore structure of the molecular sieve, changing its structure and specific surface area, so that the size and polarity of the pores are suitable for the adsorption of N 2 O molecules. and diffusion. The modified graphene/molecular sieve has shape-selective adsorption and catalysis of N 2 O while reducing the influence of H 2 O and NH 3 , as shown in Figure 5.
在较为优选的具体实施方式中,上述催化剂的制备方法,包括如下步骤:In a more preferred embodiment, the preparation method of the above catalyst includes the following steps:
石墨烯对分子筛改性方法如下:The method for modifying molecular sieves with graphene is as follows:
1)利用原位水热合成法,将蜂窝状堇青石陶瓷载体置于配置好的分子筛前驱体溶液中,在一定温度下进行原位晶化,使分子筛直接“生长”在载体上,获得分子筛涂层。1) Using the in-situ hydrothermal synthesis method, the honeycomb cordierite ceramic carrier is placed in the prepared molecular sieve precursor solution, and in-situ crystallization is performed at a certain temperature, so that the molecular sieve can be directly "grown" on the carrier to obtain the molecular sieve. coating.
2)直接在氧化石墨烯水溶液中加入水合肼,再用水热法还原制备石墨烯溶液,制得了在水中均匀、稳定分散的石墨烯溶液,避免了常规制备稳定石墨烯水溶液时表面活性剂、有机溶剂或者超酸的加入。2) Add hydrazine hydrate directly to the graphene oxide aqueous solution, and then reduce it by hydrothermal method to prepare the graphene solution. A uniform and stably dispersed graphene solution in water is obtained, which avoids the need for surfactants and organic solvents in the conventional preparation of stable graphene aqueous solutions. Addition of solvent or superacid.
3)将具有分子筛涂层的蜂窝状堇青石陶瓷载体置于石墨烯溶液中,利用超声浸渍法,将石墨烯高度分散至分子筛表面、孔道之中,完成对分子筛的表面、孔道改性,获得石墨烯/分子筛涂层。3) Place the honeycomb cordierite ceramic carrier with molecular sieve coating in the graphene solution, and use the ultrasonic impregnation method to highly disperse the graphene into the surface and pores of the molecular sieve to complete the modification of the surface and pores of the molecular sieve to obtain Graphene/molecular sieve coating.
4)进一步,重复上述步骤,可获得多层级结构的涂层。4) Further, repeat the above steps to obtain a multi-layered coating.
一种汽油机N2O零排放的催化器,由上述的催化剂封装而成。该催化器置于汽油机三元催化器之后,在汽油机排气后处理系统中的布置如图6所示。A catalytic converter for N 2 O zero emission of a gasoline engine, which is packaged by the above-mentioned catalyst. The catalytic converter is placed after the three-way catalytic converter of the gasoline engine, and its layout in the exhaust after-treatment system of the gasoline engine is shown in Figure 6.
汽油机N2O催化器的结构示意图如图7所示,图中(a)为N2O催化器;(b)表示催化器内部蜂窝状结构的径向剖视图;(c)表示中间局部轴向通道剖视图;(d)表示边界局部轴向通道剖视图;(e)表示通道局部表面结构图。The structural schematic diagram of the N 2 O catalytic converter of a gasoline engine is shown in Figure 7. In the figure (a) is the N 2 O catalytic converter; (b) shows the radial cross-sectional view of the honeycomb structure inside the catalytic converter; (c) shows the partial axial direction in the middle. Channel cross-section; (d) represents the boundary partial axial channel cross-section; (e) represents the local surface structure diagram of the channel.
技术原理如下:The technical principle is as follows:
(1)热性能(1) Thermal performance
石墨烯的热导率λ1、热扩散系数a1都要远大于分子筛的的热导率λ2、热扩散系数a2,石墨烯的比热容c1小于分子筛的比热容c2。石墨烯对分子筛改性后,石墨烯/分子筛材料的热导率λ3、热扩散系数a3、比热容c3应介于石墨烯、分子筛之间,即:The thermal conductivity λ 1 and thermal diffusion coefficient a 1 of graphene are much larger than the thermal conductivity λ 2 and thermal diffusion coefficient a 2 of molecular sieve. The specific heat capacity c 1 of graphene is smaller than the specific heat capacity c 2 of molecular sieve. After graphene has modified the molecular sieve, the thermal conductivity λ 3 , thermal diffusion coefficient a 3 , and specific heat capacity c 3 of the graphene/molecular sieve material should be between those of graphene and molecular sieve, that is:
λ2<λ3<λ1;a2<a3<a1;c1<c3<c2 λ 2 <λ 3 <λ 1 ; a 2 <a 3 <a 1 ; c 1 <c 3 <c 2
由此可提高涂层结构的的导热性能和热扩散性能,提高催化器的导热性能和热扩散性能,在同样的发动机低温起动工况条件下,可快速提高N2O催化器的内部温度。This can improve the thermal conductivity and thermal diffusion performance of the coating structure, improve the thermal conductivity and thermal diffusion performance of the catalytic converter, and quickly increase the internal temperature of the N 2 O catalytic converter under the same engine low-temperature starting conditions.
(2)稳定性(2)Stability
石墨烯具有非常稳定的蜂巢晶格结构及超疏水性,分子筛具有硅氧四面体或铝氧四面体结构,石墨烯对分子筛改性后,可提高石墨烯/分子筛材料的结构稳定性及疏水性。Graphene has a very stable honeycomb lattice structure and super hydrophobicity, and molecular sieve has a silicon-oxygen tetrahedron or aluminum-oxygen tetrahedron structure. After graphene modifies the molecular sieve, the structural stability and hydrophobicity of the graphene/molecular sieve material can be improved. .
(3)吸附性能(3) Adsorption performance
石墨烯比表面积S1要远大于分子筛比表面积S2,石墨烯对分子筛改性后,石墨烯/分子筛材料的比表面积S3应介于石墨烯、分子筛之间,即:The specific surface area S 1 of graphene is much larger than the specific surface area S 2 of molecular sieve. After the molecular sieve is modified by graphene, the specific surface area S 3 of the graphene/molecular sieve material should be between graphene and molecular sieve, that is:
S2<S3<S1 S 2 <S 3 <S 1
由此可提高N2O催化器的表面与内部吸附性能。This can improve the surface and internal adsorption performance of the N 2 O catalytic converter.
(4)催化分解过程(4) Catalytic decomposition process
汽油机N2O催化器中N2O的物理、化学过程描述示意图如图8所示,包括:催化剂载体通道涂层表面与石墨烯/分子筛结构内部纳米多孔材料中N2O的扩散、吸附过程,涂层表面与石墨烯/分子筛结构内部纳米多孔材料中N2O催化化学反应过程。The schematic diagram describing the physical and chemical processes of N 2 O in the N 2 O catalytic converter of a gasoline engine is shown in Figure 8, including: the diffusion and adsorption process of N 2 O in the nanoporous material on the surface of the catalyst carrier channel and inside the graphene/molecular sieve structure , the N 2 O catalyzed chemical reaction process between the coating surface and the nanoporous material inside the graphene/molecular sieve structure.
N2O催化分解反应为:The N 2 O catalytic decomposition reaction is:
2N2O → 2N2 + O2 (1)2N 2 O → 2N 2 + O 2 (1)
N2O在催化剂上的催化分解可能存在的反应过程为:The possible reaction processes for the catalytic decomposition of N 2 O on the catalyst are:
1)N2O吸附在贵金属催化剂T*表面,得到N2O*1) N 2 O is adsorbed on the surface of the precious metal catalyst T* to obtain N 2 O*
2)N2O*分解为N2(g)和吸附氧物种O*2) N 2 O* decomposes into N 2 (g) and adsorbed oxygen species O*
N2O*→N2+O* (3)N 2 O*→N 2 +O* (3)
3)通过Langmuir-Hinshelwood(L-H)机制,吸附氧物种重组再生空位3) Through the Langmuir-Hinshelwood (L-H) mechanism, the adsorbed oxygen species recombines and regenerates vacancies
4)N2O与吸附氧物种O*结合,得到N2(g),O2(g)和再生的贵金属催化剂T*4) N 2 O combines with the adsorbed oxygen species O* to obtain N 2 (g), O 2 (g) and regenerated precious metal catalyst T*
N2O+O*→N2+O2+T* (5)N 2 O+O*→N 2 +O 2 +T* (5)
5)N2O吸附在贵金属催化剂T*表面发生反应,得到N2(g)和吸附氧物种O*5) N 2 O is adsorbed on the surface of the precious metal catalyst T* and reacts to obtain N 2 (g) and adsorbed oxygen species O*
N2O+T*→N2+O* (6)N 2 O+T*→N 2 +O* (6)
吸附过程的能量变化ΔEads:Energy change ΔE ads during adsorption process:
ΔEads=Ecatalyst+adsorbate-(Ecatalyst+Eadsorbate) (7)ΔE ads =E catalyst+adsorbate -(E catalyst +E adsorbate ) (7)
式中,Ecatalyst+adsorbate为催化剂吸附了吸附质的能量,Ecatalyst是催化剂的能量,Eadsorbate是吸附质的能量。In the formula, E catalyst+adsorbate is the energy of the adsorbate adsorbed by the catalyst, E catalyst is the energy of the catalyst, and E adsorbate is the energy of the adsorbate.
反应过程的活化能ΔE:Activation energy ΔE of the reaction process:
ΔE=ETS-EIS (8)ΔE=E TS -E IS (8)
式中,EIS是初始状态的总能量,ETS是过渡态的总能量。In the formula, E IS is the total energy of the initial state, and E TS is the total energy of the transition state.
反应速率常数:Reaction rate constant:
式中,kB是玻耳兹曼常数,h是普朗克常数,R是通用气体常数,T是温度,ΔE是反应活化能。In the formula, k B is Boltzmann's constant, h is Planck's constant, R is the universal gas constant, T is the temperature, and ΔE is the reaction activation energy.
本发明中提供的汽油机N2O零排放催化剂及催化器,具有如下优点:The gasoline engine N 2 O zero emission catalyst and catalytic converter provided by the present invention have the following advantages:
(1)石墨烯对分子筛改性的石墨烯/分子筛的多层级交错结构,改变了涂层的孔隙结构,增加了材料的比表面积,有利于增加N2O的吸附能力。(1) The multi-level staggered structure of graphene/molecular sieve modified by graphene changes the pore structure of the coating, increases the specific surface area of the material, and is beneficial to increasing the adsorption capacity of N 2 O.
(2)根据N2O分子的大小与极性,利用石墨烯分子的结构可调控性,改变分子筛的孔隙结构与吸附极性,使改性后的改变了石墨烯/分子筛孔隙结构对N2O具有择形催化性。(2) According to the size and polarity of N 2 O molecules, the structural controllability of graphene molecules is used to change the pore structure and adsorption polarity of molecular sieves, so that the modified graphene/molecular sieve pore structure changes the effect of N 2 O has shape-selective catalysis.
(3)多层级交错结构以及增加的材料比表面积可改变N2O在孔隙结构中的扩散性能,延长扩散时间,有利于催化剂有足够的时间提高温度,达到N2O催化分解的温度。(3) The multi-level staggered structure and the increased specific surface area of the material can change the diffusion performance of N 2 O in the pore structure and extend the diffusion time, which will help the catalyst have enough time to increase the temperature and reach the temperature for N 2 O catalytic decomposition.
(4)多层级交错结构的石墨烯/分子筛中,石墨烯非常好的热传导和热扩散性,较低的比热容,有利于催化剂内部的热扩散和温度的升高,缩短催化剂的起燃时间。(4) In the multi-level staggered structure of graphene/molecular sieve, graphene has very good thermal conductivity and thermal diffusivity, and a low specific heat capacity, which is beneficial to the thermal diffusion and temperature increase inside the catalyst, and shortens the ignition time of the catalyst.
(5)Rh催化剂、CeO2助催化剂的多层级交错结构增加了催化剂的内部活性点位,可提高催化剂内部的储氧、释氧调控能力以及N2O的催化性能。(5) The multi-level staggered structure of Rh catalyst and CeO 2 cocatalyst increases the internal active sites of the catalyst, which can improve the oxygen storage and oxygen release control capabilities inside the catalyst and the catalytic performance of N 2 O.
以上所述实施例仅表达了本申请的几种实施方式,其描述较为具体和详细,但并不能因此而理解为对申请专利范围的限制。应当指出的是,对于本领域的普通技术人员来说,在不脱离本申请构思的前提下,还可以做出若干变形和改进,这些都属于本申请的保护范围。因此,本申请专利的保护范围应以所附权利要求为准。The above-described embodiments only express several implementation modes of the present application, and their descriptions are relatively specific and detailed, but they should not be construed as limiting the scope of the patent application. It should be noted that, for those of ordinary skill in the art, several modifications and improvements can be made without departing from the concept of the present application, and these all fall within the protection scope of the present application. Therefore, the protection scope of this patent application should be determined by the appended claims.
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Citations (14)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN102133537A (en) * | 2010-12-29 | 2011-07-27 | 浙江工业大学 | Honeycomb-ceramic-type monolithic catalyst, and preparation method and application thereof |
| CN103127949A (en) * | 2011-12-01 | 2013-06-05 | 上海纳米技术及应用国家工程研究中心有限公司 | Scavenging material with molecular sieve integral type oxynitride and preparation method |
| US20130192461A1 (en) * | 2012-01-27 | 2013-08-01 | Empire Technology Development, Llc | Accelerating transport through graphene membranes |
| CN103418374A (en) * | 2013-08-15 | 2013-12-04 | 中南大学 | Metal catalyst with cordierite coated with graphene on the surface as carrier and preparation of metal catalyst |
| US20140112854A1 (en) * | 2012-10-19 | 2014-04-24 | Basf Corporation | 8-Ring Small Pore Molecular Sieve as High Temperature SCR Catalyst |
| CN104492473A (en) * | 2014-12-30 | 2015-04-08 | 华东理工大学 | Molecular sieve-coating cerium oxide composite material and preparation method thereof |
| KR20150097308A (en) * | 2014-02-18 | 2015-08-26 | 한국생산기술연구원 | Fabrication method of SCR catalyst added carbon material supported vanadium |
| CN104888841A (en) * | 2015-05-26 | 2015-09-09 | 华东理工大学 | Preparation method of monolithic catalyst with molecular sieve type coating |
| CN106475132A (en) * | 2016-10-11 | 2017-03-08 | 中国科学院山西煤炭化学研究所 | A kind of Graphene/molecular sieve/metal-oxide composite catalyst and preparation method thereof |
| CN106824296A (en) * | 2016-12-30 | 2017-06-13 | 尹宗杰 | A kind of porous graphene zeolite molecular sieve catalyst carrier and preparation method thereof |
| CN107737526A (en) * | 2017-10-25 | 2018-02-27 | 成都新柯力化工科技有限公司 | The graphene catalytic plate and preparation method of a kind of high-efficient purification vehicle exhaust |
| CN108192486A (en) * | 2017-12-31 | 2018-06-22 | 江苏万源新材料股份有限公司 | A kind of graphene molecules sieve coated aluminum foil and preparation method thereof |
| CN110787769A (en) * | 2019-10-18 | 2020-02-14 | 南京领丰新材料科技有限公司 | Graphene-based VOCs (volatile organic compounds) removing self-assembled coated cloth/paper and preparation method thereof |
| CN115055162A (en) * | 2022-06-21 | 2022-09-16 | 广东恒峰蓝环境工程有限公司 | Preparation method of zeolite molecular sieve adsorption material |
-
2023
- 2023-06-20 CN CN202310730653.4A patent/CN116809111A/en active Pending
Patent Citations (14)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN102133537A (en) * | 2010-12-29 | 2011-07-27 | 浙江工业大学 | Honeycomb-ceramic-type monolithic catalyst, and preparation method and application thereof |
| CN103127949A (en) * | 2011-12-01 | 2013-06-05 | 上海纳米技术及应用国家工程研究中心有限公司 | Scavenging material with molecular sieve integral type oxynitride and preparation method |
| US20130192461A1 (en) * | 2012-01-27 | 2013-08-01 | Empire Technology Development, Llc | Accelerating transport through graphene membranes |
| US20140112854A1 (en) * | 2012-10-19 | 2014-04-24 | Basf Corporation | 8-Ring Small Pore Molecular Sieve as High Temperature SCR Catalyst |
| CN103418374A (en) * | 2013-08-15 | 2013-12-04 | 中南大学 | Metal catalyst with cordierite coated with graphene on the surface as carrier and preparation of metal catalyst |
| KR20150097308A (en) * | 2014-02-18 | 2015-08-26 | 한국생산기술연구원 | Fabrication method of SCR catalyst added carbon material supported vanadium |
| CN104492473A (en) * | 2014-12-30 | 2015-04-08 | 华东理工大学 | Molecular sieve-coating cerium oxide composite material and preparation method thereof |
| CN104888841A (en) * | 2015-05-26 | 2015-09-09 | 华东理工大学 | Preparation method of monolithic catalyst with molecular sieve type coating |
| CN106475132A (en) * | 2016-10-11 | 2017-03-08 | 中国科学院山西煤炭化学研究所 | A kind of Graphene/molecular sieve/metal-oxide composite catalyst and preparation method thereof |
| CN106824296A (en) * | 2016-12-30 | 2017-06-13 | 尹宗杰 | A kind of porous graphene zeolite molecular sieve catalyst carrier and preparation method thereof |
| CN107737526A (en) * | 2017-10-25 | 2018-02-27 | 成都新柯力化工科技有限公司 | The graphene catalytic plate and preparation method of a kind of high-efficient purification vehicle exhaust |
| CN108192486A (en) * | 2017-12-31 | 2018-06-22 | 江苏万源新材料股份有限公司 | A kind of graphene molecules sieve coated aluminum foil and preparation method thereof |
| CN110787769A (en) * | 2019-10-18 | 2020-02-14 | 南京领丰新材料科技有限公司 | Graphene-based VOCs (volatile organic compounds) removing self-assembled coated cloth/paper and preparation method thereof |
| CN115055162A (en) * | 2022-06-21 | 2022-09-16 | 广东恒峰蓝环境工程有限公司 | Preparation method of zeolite molecular sieve adsorption material |
Non-Patent Citations (2)
| Title |
|---|
| 胡丽;王改;薄琼;杨冬花;赵煜;董志帅;: "石墨烯改性NiY分子筛的合成及催化析氢性能研究", 化工新型材料, no. 05, 15 May 2019 (2019-05-15), pages 102 - 105 * |
| 龙湘犁等: "环境科学与工程概论", 31 August 2007, 华东理工大学出版社, pages: 90 - 91 * |
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