The present application relates to the technical field of noble metal-loading catalysts, and in particular relates to a grain boundary and surface-loaded noble metal catalyst and a honeycomb noble metal catalyst, as well as a preparation method and an application thereof.
In recent years, rare-ignition engines (diesel and rare-ignition gasoline engines) have received wide attention due to their high fuel economy and low greenhouse gas emissions. However, NOx, CO and HC emitted from the exhaust of dilute combustion engines pose a serious threat to human health. At present, the environmental protection requirements for diesel exhaust are becoming more and more stringent by governments all over the world. In terms of the mechanism of the reaction, HC and CO are easily oxidized and removed under aerobic conditions, whereas the NOx reaction is more complicated, which needs a highly efficient catalyst with high oxygen storage capacity and high low-temperature activity to achieve better elimination. When driving at high speeds, the temperature of diesel exhaust can reach as high as 600° C. or more, so the catalyst is also required to have high activity at high temperatures. The noble metals of catalysts in the prior art are easily agglomerated and poorly dispersed at high temperatures, which cannot effectively treat diesel exhaust and therefore cause environmental pollution, so there is an urgent need for the development of efficient catalysts for purification of diesel exhaust NOx with high stability and high activity.
Diesel oxidation catalysts (DOC) have received much attention in recent years, and the powerful NO oxidizability of DOC can greatly improve SCR low-temperature NOx conversion (Russell A, Epling W S. Catalysis Reviews, 2011, 53 (4): 337-423). Currently, commercial DOC catalysts have many drawbacks, such as the tendency of agglomerative deactivation of noble metals at high temperatures and high reaction temperatures (Caliskan H, Mori K. Energy, 2017, 128. 128-144). Therefore, the study of DOC catalysts with high noble metal dispersion and high activity has become the focus of diesel post-treatment systems. In order to obtain a higher NO catalytic oxidation performance, it is necessary to develop a highly stable and active DOC catalyst.
Based on the above situation of the prior art, the present application aims to provide a grain boundary and surface-loaded noble metal catalyst and a preparation method and an application thereof, wherein, the noble metal is dispersed at the grain boundary and surface of alumina and/or a rare earth manganese-zirconium composite oxide to form a multiphase interface, which can inhibit the migration, agglomeration, and growth of the noble metal at high temperatures, increase the high-temperature stability and catalytic performance of the noble metal, and reduce the usage of the noble metal; which can also reduce the activation energy of lattice oxygen and increase the quantity of active oxygen, thereby enhancing the NO oxidation and low-temperature catalytic activity.
To achieve the above object, according to a first aspect of the present application, provided is a grain boundary and surface-loaded noble metal catalyst comprising a noble metal G, alumina and/or a rare earth manganese-zirconium composite oxide, wherein the noble metal G is dispersed at the grain boundary and surface of alumina and/or the rare earth manganese-zirconium composite oxide, and the rare earth manganese-zirconium composite oxide has the formula of REaMnbZrcMdO(2-δ)Dβ, where,
According to a second aspect of the present application, provided is a honeycomb noble metal catalyst comprising a honeycomb carrier, a noble metal G, and an active coating, wherein the active coating contains alumina and/or the rare earth manganese-zirconium composite oxide REaMnbZrcMdO(2-δ)Dβ, and the noble metal G is dispersed at the grain boundary and surface of the active coating, where
Further, the rare earth manganese-zirconium composite oxide accounts for 0 to 100%, preferably 30 to 70%, of the total mass of the active coating.
Further, the noble metal G at the grain boundary and surface is in a metallic state, or in a metallic and oxidization state.
Further, the noble metal G comprises one or a combination of more than one of Pt, Pd, Rh, Ir, Os, Ru, Au, and Ag, preferably one or a combination of more than one of Pt, Pd, Rh, and Ru, further preferably a combination of Pt and Pd.
Further, the rare earth element RE comprises one or a combination of more than one of La, Ce, Pr, Nd, Sm, Eu, Gd, Tb, Dy, Ho, Er, Tm, Yb, Lu, Y, and Sc, preferably one or a combination of more than one of La, Ce, Pr, Nd, Sm, Eu, Gd, Yb, and Y; the doping element M is one or a combination of more than one of a transition metal element, an alkaline earth metal elements, Al, Si, and Sn; the doping element D comprises one or a combination of more than one of anions N, P, and F.
Further, the transition metal element M comprises one or a combination of more than one of Fe, Co, Ni, Cu, Zn, Ti, Hf, V, Cr, Nb, Mo, and W, preferably one or a combination of more than one of Fe, Co, Ni, Cu, and Hf; the alkaline earth metal element is one or a combination of more than one of Mg, Ca, Sr, and Ba, preferably one or a combination of more than one of Sr and Ba.
Further, the loading amount of the noble metal G in the catalyst is 0.01% to 2% by mass, preferably 0.1% to 1% by mass.
Further, the loading amount of the noble metal G in the catalyst is 0.03 to 2.0 g/L, preferably 0.15 to 1.5 g/L.
Further, the rare earth manganese-zirconium composite oxide in the catalyst comprises a core-shell structure having an inner core comprising a rare earth and zirconium element and an outer shell comprising a rare earth and manganese element.
Further, the rare earth manganese-zirconium composite oxide in the catalyst comprises a rare earth zirconium-based oxide with gradient distribution of elements.
Further, the honeycomb carrier is made of a porous ceramic or metal, and further, the honeycomb carrier may be one or a combination of more than one of cordierite, cordierite-alumina, silicon nitride, silicon carbide, alumina-silica-magnesium oxide, zirconium silicate-sillimanite, magnesium silicate, and aluminum silicate.
According to a third aspect of the present application, there is provided a method for preparing the grain boundary and surface-loaded noble metal catalyst of the first aspect of the application, comprising the steps of:
According to a fourth aspect of the present application, there is provided a method for preparing the honeycomb noble metal catalyst of the second aspect of the present application, wherein the honeycomb noble metal catalyst is layered or partitioned coated with one or more coating materials selected from alumina, a rare earth manganese-zirconium composite oxide, alumina with the boundary and surface loaded with the noble metal, the rare earth manganese-zirconium composite oxide with the grain boundary and surface loaded with the noble metal, and a mixture of rare earth manganese-zirconium composite oxide and alumina with their grain boundaries and surfaces loaded with the noble metal, the method comprising the steps of:
According to a fifth aspect of the present application, there is provided a method for preparing the honeycomb noble metal catalyst of the second aspect of the present application, the method comprising: preparing a coating slurry by mixing the rare earth manganese-zirconium composite oxide and/or alumina, a liquid salt of the noble metal, an adhesive, an acidity regulator and water evenly in one or more steps; coating the obtained slurry onto a honeycomb carrier in one or more steps, or onto the honeycomb carrier in a layered or partitioned manner, and drying; performing heat treatment and/or calcination on the dried honeycomb carrier under air or a reducing atmosphere, to obtain the honeycomb catalyst with the grain boundary and surface loaded with the noble metal.
Further, the heat treatment temperature is 200 to 750° C., and the heat treatment time is 0.5 h to 24 h; preferably, the heat treatment temperature is 400 to 700° C., and preferably, the heat treatment time is 1 h to 12 h.
Further, the calcination temperature is 400 to 850° C., and the calcination time is 0.5 h to 24 h; preferably, the calcination temperature is 450 to 750° C., and the calcination time is 1 h to 12 h.
Further, the liquid salt of the noble metal G comprises one or a combination of more than one molten salt or aqueous solution of chlorate, nitrate, acetate, and citrate.
Further, the reducing atmosphere comprises one or more of CO and H2.
According to a sixth aspect of the present application, there is provided use of the catalysts in the first and second aspects of the present application in the fields of vehicle exhaust purification, industrial organic exhaust treatment, catalytic combustion of natural gas, petrochemicals, hydrogen energy, and batteries.
In summary, the present application provides a grain boundary and surface-loaded noble metal catalyst and a preparation method and an application thereof, wherein the noble metal G is dispersed at the grain boundary and surface of alumina and/or a rare earth manganese-zirconium composite oxide to form a multiphase interface, which achieves the following beneficial technical effects: firstly, the multiphase interface has a larger steric hindrance and a stronger anchoring effect, which can inhibit the migration, agglomeration, and growth of the noble metal at high temperatures, increase the high-temperature stability and catalytic performance of the noble metal, and reduce the usage of the noble metal; secondly, the multiphase interface exhibits a synergistic catalytic effect, which can reduce the activation energy of lattice oxygen and increase the quantity of active oxygen, thereby enhancing the NO oxidation and low-temperature catalytic activity. Moreover, according to the present application, the types and contents of elements in the outer shell and/or inner core are designed based on theoretically calculated differences in elemental surface energy and oxygen vacancy formation energy, which comprehensively improves the thermal stability and oxygen storage and release properties of the rare earth manganese-zirconium composite oxide; still, the types and contents of elements in the gradient structure are designed based on theoretically calculated differences in elemental surface energy and oxygen vacancy formation energy, such that the content of a specific element increases or decreases gradually from inside to outside in the radial direction of grains, thus comprehensively improving the thermal stability and oxygen storage and release properties of the rare earth cerium-zirconium composite oxide.
In order to make the purpose, technical solutions and advantages of the application clearer, the application will be further explained in detail below in connection with the embodiments with reference to the drawings. It should be understood that these descriptions are merely exemplary and are not intended to limit the scope of the application. In addition, descriptions of well-known structures and techniques are omitted below to avoid unnecessary confusion about the concepts of the present application.
Examples of the present application provide a grain boundary and surface-loaded noble metal catalyst comprising a noble metal G, alumina and/or a rare earth manganese-zirconium composite oxide, wherein, the noble metal G is dispersed at the grain boundary and surface of alumina and/or the rare earth manganese-zirconium composite oxide. The simultaneous presence of the noble metal G at both the grain boundary and the surface can not only fully utilize the new site loading the noble metal at the grain boundary, but also reduce the distribution density of the noble metal loaded at the surface, thereby forming a grain boundary-surface double-anchoring structure, which not only can inhibit the migration and agglomeration of the noble metal at high temperatures but also can improve the thermal stability of the noble metal. The rare earth manganese-zirconium composite oxide has the chemical formula REaMnbZrcMdO(2-δ)Dβ, where
Examples of the present application also provides a honeycomb noble metal catalyst comprising a honeycomb carrier, a noble metal G, and a active coating comprising alumina and/or a rare earth manganese-zirconium composite oxide REaMnbZrcMdO(2-δ)DB, wherein, the noble metal G is dispersed at the grain boundary and surface of the active coating. The simultaneous presence of the noble metal G at both the grain boundary and the surface of the active coating can not only fully utilize the new site loading the noble metal at the grain boundary, but also reduce the distribution density of the noble metal loaded at the surface, thereby forming a grain boundary-surface double-anchoring structure, which not only can inhibit the migration and agglomeration of the noble metal at high temperatures but also can improve the thermal stability of the noble metal, where
The noble metal G may be, for example, one or a combination of more than one of Pt, Pd, Rh, Ir, Os, Ru, Au, and Ag, preferably one or a combination of more than one of Pt, Pd, Rh, and Ru, further preferably a combination of Pt and Pd; the noble metal G at the grain boundary accounts for 10-70 mol %; the noble metal G at the grain boundary or surface is in a metallic state, or in a metallic and oxidization state. Preferably, converting to a metallic state is more conductive to the catalytic effect. In the grain boundary and surface-loaded noble metal catalyst, the loading amount of the noble metal G is 0.01% to 2% by mass, preferably 0.1% to 1% by mass, further preferably 0.1% to 0.5% by mass. In the honeycomb noble metal catalyst, the loading amount of the noble metal G is 0.03 to 2.0 g/L, preferably 0.15 to 1.5 g/L. The rare earth manganese-zirconium composite oxide accounts for 0 to 100%, preferably 30 to 70%, of the in total mass of the active coating.
In the grain boundary and surface-loaded noble metal catalyst and the honeycomb noble metal catalyst provided by examples of the present applications, the noble metal is dispersed at the grain boundary and surface of alumina and/or the rare earth manganese-zirconium composite oxide to form a multiphase interface. The multiphase interface has a larger steric hindrance and a stronger anchoring effect, which can inhibit the migration, agglomeration, and growth of the noble metal at high temperatures, increase the high-temperature stability and catalytic performance of the noble metal, and reduce the usage of the noble metal. The multiphase interface also exhibits a synergistic catalytic effect, which can reduce the activation energy of lattice oxygen and increase the quantity of active oxygen, thereby enhancing the NO oxidation and low-temperature catalytic activity.
The rare earth manganese-zirconium composite oxide in the catalyst provided by the examples of the present application comprises a core-shell structure having an inner core comprising a rare earth and zirconium element and an outer shell comprising a rare earth and manganese element. For additional features and advantages of the core-shell structure of a rare earth manganese-zirconium composite oxide, please refer to the Chinese Patent Application with the application number of ZL201910833257.8 and the application title of “Rare earth manganese-zirconium composite oxide with core-shell structure, and preparation method thereof” filed on Sep. 4, 2019 and its full description. According to the present application, the types and contents of shell or/and core elements are designed based on theoretically calculated differences in elemental surface energy and oxygen vacancy formation energy to comprehensively enhance the thermal stability and oxygen storage and release properties of the rare earth manganese-zirconium composite oxide.
The rare earth manganese-zirconium composite oxide in the catalyst provided by examples of the present application, comprises a rare earth zirconium-based oxide with gradient distribution of elements. For additional features and advantages of the gradient distribution of elements of the rare earth zirconium-based oxide, please refer to the Chinese Patent Application with the application number of CN202010982979.2 and the application title of “Cerium-zirconium-based composite oxide with elements in gradient distribution and preparation method thereof” filed on Sep. 17, 2020 and its full description. According to the present application, the types and contents of elements in the gradient structure are designed and controlled based on theoretically calculated differences in elemental surface energy and oxygen vacancy formation energy, so that the content of a specific element increases or decreases gradually from inside to outside in the radial direction of grains, thus comprehensively improving the thermal stability and the oxygen storage and release properties of the rare earth manganese-zirconium composite oxide.
The rare earth element RE in the rare earth manganese-zirconium composite oxide comprises one or a combination of more than one of La, Ce, Pr, Nd, Sm, Eu, Gd, Tb, Dy, Ho, Er, Tm, Yb, Lu, Y, and Sc, preferably one or a combination of more than one of La, Ce, Pr, Nd, Sm, Eu, Gd, Yb, and Y. The doping element M is one or a combination of more than one of a transition metal element, an alkaline earth metal elements, Al, Si, and Sn; the doping element D comprises one or a combination of more than one of anions N, P, and F.
In the rare earth manganese-zirconium composite oxide, the transition metal element M comprises one or a combination of more than one of Fe, Co, Ni, Cu, Zn, Ti, Hf, V, Cr, Nb, Mo, and W, preferably one or a combination of more than one of Fe, Co, Ni, Cu, and Hf; the alkaline earth metal element is one or a combination of more than one of Mg, Ca, Sr, and Ba, preferably one or a combination of more than one of Sr and Ba.
Examples of the present application also provide a method for preparing a grain boundary and surface-loaded noble metal catalyst to prepare the grain boundary and surface-loaded noble metal catalyst in the above examples, with the flow chart of the method shown in
In performing heat treatment in step S2 in the above examples, the grain boundaries of the rare earth manganese-zirconium composite oxide and/or alumina start to be activated by controlling the appropriate temperature, thereby serving as channels for noble metal diffusion, and the depth and distribution of noble metal diffusion along the grain boundary can be controlled by controlling the heat treatment time. The noble metals at the grain boundary and surface can be reduced or partially reduced by controlling the reducing atmosphere, the reducing temperature, and the reducing time in step S3. The noble metal is dispersed at the grain boundary and surface of alumina and/or the rare earth manganese-zirconium composite oxide by steps S2 and S3 to form a multiphase interface. The multiphase interface has a larger steric hindrance and a stronger anchoring effect, which can inhibit the migration, agglomeration, and growth of the noble metal at high temperatures, increase the high-temperature stability and catalytic performance of the noble metal, and reduce the usage of the noble metal. The multiphase interface also exhibits a synergistic catalytic effect, which can reduce the activation energy of lattice oxygen and increase the quantity of active oxygen, thereby enhancing the NO oxidation and low-temperature catalytic activity.
The examples of the present application further provide a method for preparing a honeycomb noble metal catalyst to prepare the honeycomb noble metal catalyst provided in the above examples, wherein the honeycomb noble metal catalyst is layered or partitioned coated with one or more coating materials selected from alumina, a rare earth manganese-zirconium composite oxide, alumina with the boundary and surface loaded with the noble metal, a rare earth manganese-zirconium composite oxide with the grain boundary and surface loaded with the noble metal, and a mixture of rare earth manganese-zirconium composite oxide and alumina with their grain boundaries and surfaces loaded with the noble metal, with the flow chart of the method shown in
Examples of the present application further provide a method for preparing a honeycomb noble metal catalyst to prepare the honeycomb noble metal catalyst provided in the above examples, the method comprising: preparing a coating slurry by mixing a rare earth manganese-zirconium composite oxide and/or alumina, a liquid salt of the noble metal, an adhesive, an acidity regulator and water evenly in one or more steps; coating the obtained slurry onto a honeycomb carrier in one or more steps, or onto the honeycomb carrier in a layered or partitioned manner, and drying; performing heat treatment and/or calcination on the dried honeycomb carrier under air or a reducing atmosphere, to obtain the honeycomb catalyst with the grain boundary and surface loaded with the noble metal.
The examples of the present application provide a grain boundary and surface-loaded noble metal catalyst and a honeycomb noble metal catalyst, respectively, wherein the noble metal is dispersed at the grain boundary and surface of alumina and/or a rare earth manganese-zirconium composite oxide to form a multiphase interface. The multiphase interface has a larger steric hindrance and a stronger anchoring effect, which can inhibit the migration, agglomeration, and growth of the noble metal at high temperatures, increase the high-temperature stability and catalytic performance of the noble metal, and reduce the usage of the noble metal. The multiphase interface also exhibits a synergistic catalytic effect, which can reduce the activation energy of lattice oxygen and increase the quantity of active oxygen, thereby enhancing the low-temperature catalytic activity for NO oxidation.
The examples of the present application also provide use of the grain boundary and surface-loaded noble metal catalyst and the honeycomb noble metal catalyst described above in the fields of vehicle exhaust purification, industrial organic exhaust treatment, catalytic combustion of natural gas, petrochemicals, hydrogen energy, and batteries. The grain boundary and surface-loaded noble metal catalyst and the honeycomb noble metal catalyst provided by the examples of the present application have superior low-temperature catalytic activity for NO oxidation and better high-temperature stability, and thus can satisfy the application requirements in relevant various fields.
The present application will be further described in below with reference to specific examples.
A certain volume of platinum nitrate liquid salt was weighed according to a Pt loading amount of 0.2 wt % and mixed well with solid powders of the rare earth manganese-zirconium composite oxide Ce0.10Mn0.05Y0.05Zr0.80O2. The resulting mixture was dried at 120° C. for 10 hours, and then subjected to calcination under air atmosphere at 700° C. for 3 hours, to give the catalyst Pt (0.2 wt %)/Ce0.10Mn0.05Y0.05Zr0.80O2. The above catalyst was tested for catalytic performance, and the resulting maximum NO conversion was 63.52%, the temperature at which the maximum NO conversion occurred was 326° C. After 650° C./10% H2O/100 h hydrothermal aging, the maximum NO conversion of the catalyst was 49.38%.
A certain volume of platinum nitrate liquid salt was weighed according to a Pt loading amount of 0.2 wt % and mixed well with solid powders of the rare earth manganese-zirconium composite oxide Ce0.20Mn0.05Y0.05Zr0.70O1.99. The resulting mixture was dried at 100° C. for 6 hours, and then subjected to calcination under air atmosphere at 600° C. for 6 hours, to give the catalyst Pt (0.2 wt %)/Ce0.20Mn0.05Pr0.05Zr0.70O1.99. The above catalyst was tested for catalytic performance, and the resulting maximum NO conversion was 64.06%, the temperature at which the maximum NO conversion occurred was 324° C. After 650° C./10% H2O/100 h hydrothermal aging, the maximum NO conversion of the catalyst was 50.37%.
A certain volume of platinum nitrate liquid salt was weighed according to a Pt loading amount of 1.1 g/L, to which was added Al2O3, Ce0.30Mn0.25La0.05Nd0.05W0.05Zr0.30O1.99, an acidity regulator and water and mixed well before adding an adhesive and mixing well, to prepare a slurry. The slurry was coated onto a cordierite ceramic honeycomb carrier. The coated carrier was dried at 80° C. for 8 hours and subjected to calcination under H2 reducing atmosphere at 600° C. for 3 hours to give the honeycomb noble metal catalyst Pt (1.1 g/L)/Ce0.30Mn0.25La0.05Nd0.05W0.05Zr0.30O1.99—Al2O3. The above catalyst was tested for catalytic performance, and the resulting maximum NO conversion was 65.54%, the temperature at which the maximum NO conversion occurred was 330° C. After 650° C./10% H2O/100 h hydrothermal aging, the maximum NO conversion of the catalyst was 50.93%.
A certain volume of platinum nitrate liquid salt was weighed according to a Pt loading amount of 0.2 wt % and mixed well with solid powders of the rare earth manganese-zirconium composite oxide Ce0.10Mn0.05 Y0.05Zr0.80O2. The resulting mixture was dried at 120° C. for 10 hours, and subjected to heat treatment at 500° C. for 3 hours and then calcination under H2 reducing atmosphere at 700° C. for 3 hours, to give the catalyst Pt (0.2 wt %)/Ce0.10Mn0.05Y0.05Zr0.80O2. The noble metal Pt was dispersed at the grain boundary and surface of the rare earth manganese-zirconium composite oxide. The above catalyst was tested for catalytic performance, and the resulting maximum NO conversion was 71.44%, the temperature at which the maximum NO conversion occurred was 283° C. After 650° C./10% H2O/100 h hydrothermal aging, the maximum NO conversion of the catalyst was 60.13%.
A certain volume of platinum nitrate liquid salt was weighed according to a Pt loading amount of 0.2 wt % and mixed well with solid powders of the rare earth manganese-zirconium composite oxide Ce0.20Mn0.05Pr0.05Zr0.70O1.99. The resulting mixture was dried at 100° C. for 6 hours, and then subjected to heat treatment at a low temperature of 200° C. for 6 hours, another heat treatment at a high temperature of 500° C. for 2 hours, and calcination under H2 reducing atmosphere at 600° C. for 6 hours, to give the catalyst Pt (0.2 wt %)/Ce0.20Mn0.05Pr0.05Zr0.70O1.99. The noble metal Pt was dispersed at the grain boundary and surface of the rare earth manganese-zirconium composite oxide. The above catalyst was tested for catalytic performance, and the resulting maximum NO conversion was 75.52%, the temperature at which the maximum NO conversion occurred was 273° C. After 650° C./10% H2O/100 h hydrothermal aging, the maximum NO conversion of the catalyst was 65.31%.
A certain volume of platinum nitrate liquid salt was weighed according to a Pt loading amount of 0.2 wt % and mixed well with solid powders of the rare earth manganese-zirconium composite oxide Ce0.20Mn0.10Yb0.10Zr0.60O1.99. The resulting mixture was dried at 110° C. for 12 hours, and then subjected to heat treatment at 530° C. for 3 hours, and calcination under H2 reducing atmosphere at 650° C. for 3 hours, to give the catalyst Pt (0.2 wt %)/Ce0.20Mn0.10Yb0.10Zr0.60O1.99. The noble metal Pt was dispersed at the grain boundary and surface of the rare earth manganese-zirconium composite oxide. The above catalyst was tested for catalytic performance, and the resulting maximum NO conversion was 73.54%, the temperature at which the maximum NO conversion occurred was 277° C. After 650° C./10% H2O/100 h hydrothermal aging, the maximum NO conversion of the catalyst was 63.54%.
A certain volume of platinum nitrate liquid salt was weighed according to a Pt loading amount of 0.2 wt % and mixed well with solid powders of the rare earth manganese-zirconium composite oxide Ce0.20Mn0.10Gd0.20Zr0.50O1.99. The resulting mixture was dried at 90° C. for 23 hours, and then subjected to heat treatment at 530° C. for 3 hours, and calcination at 650° C. for 3 hours, to give the catalyst Pt (0.2 wt %)/Ce0.20Mn0.10Gd0.20Zr0.50O1.99. The noble metal Pt was dispersed at the grain boundary and surface of the rare earth manganese-zirconium composite oxide. The above catalyst was tested for catalytic performance, and the resulting maximum NO conversion was 74.78%, the temperature at which the maximum NO conversion occurred was 273° C. After 650° C./10% H2O/100 h hydrothermal aging, the maximum NO conversion of the catalyst was 64.43%.
A certain volume of chloroplatinic acid solution was weighed according to a Pt loading amount of 0.3 wt % and mixed well with solid powders of the rare earth manganese-zirconium composite oxide Ce0.20Mn0.15Eu0.15Zr0.50O1.99. The resulting mixture was washed and dried at 100° C. for 13 hours, and then subjected to heat treatment at 530° C. for 3 hours, and calcination under H2 reducing atmosphere at 650° C. for 3 hours, to give the catalyst Pt (0.3 wt %)/Ce0.20Mn0.15Eu0.15Zr0.50O1.99. The noble metal Pt was dispersed at the grain boundary and surface of the rare earth manganese-zirconium composite oxide. The above catalyst was tested for catalytic performance, and the resulting maximum NO conversion was 76.63%, the temperature at which the maximum NO conversion occurred was 267° C. After 650° C./10% H2O/100 h hydrothermal aging, the maximum NO conversion of the catalyst was 65.16%.
A certain volume of platinum nitrate liquid salt was weighed according to a Pt loading amount of 0.4 wt % and mixed well with solid powders of the rare earth manganese-zirconium composite oxide Ce0.20Mn0.15 La0.15Zr0.50O1.99. The resulting mixture was dried at 80° C. for 9 hours, and then subjected to heat treatment at a low temperature of 300° C. for 5 hours, heat treatment at a high temperature of 550° C. for 3 hours, and calcination under H2 reducing atmosphere at 650° C. for 5 hours, to give the catalyst Pt (0.4 wt %)/Ce0.20Mn0.15La0.15Zr0.50O1.99. The noble metal Pt was dispersed at the grain boundary and surface of the rare earth manganese-zirconium composite oxide. The above catalyst was tested for catalytic performance, and the resulting maximum NO conversion was 77.33%, the temperature at which the maximum NO conversion occurred was 261° C. After 650° C./10% H2O/100 h hydrothermal aging, the maximum NO conversion of the catalyst was 66.46%.
A certain volume of platinum nitrate liquid salt was weighed according to a Pt loading amount of 0.4 wt % and mixed well with solid powders of the rare earth manganese-zirconium composite oxide Ce0.20Mn0.15Nd0.15Zr0.50O1.99. The resulting mixture was dried at 110° C. for 15 hours, and then subjected to heat treatment at 550° C. for 5 hours, and calcination under H2 reducing atmosphere at 650° C. for 5 hours, to give the catalyst Pt (0.4 wt %)/Ce0.20Mn0.15Nd0.15Zr0.50O1.99. The noble metal Pt was dispersed at the grain boundary and surface of the rare earth manganese-zirconium composite oxide. The above catalyst was tested for catalytic performance, and the resulting maximum NO conversion was 77.34%, the temperature at which the maximum NO conversion occurred was 266° C. After 650° C./10% H2O/100 h hydrothermal aging, the maximum NO conversion of the catalyst was 66.68%.
A certain volume of platinum nitrate liquid salt was weighed according to a Pt loading amount of 0.4 wt % and mixed well with solid powders of the rare earth manganese-zirconium composite oxide Ce0.20Mn0.15La0.15Zr0.50O1.99. The resulting mixture was dried at 90° C. for 10 hours, and then subjected to heat treatment at 550° C. for 5 hours, and calcination under H2 reducing atmosphere at 650° C. for 5 hours, to give the catalyst Pt (0.4 wt %)/Ce0.20Mn0.15La0.15Zr0.50O1.99. The noble metal Pt was dispersed at the grain boundary and surface of the rare earth manganese-zirconium composite oxide. The above catalyst was tested for catalytic performance, and the resulting maximum NO conversion was 76.91%, the temperature at which the maximum NO conversion occurred was 267° C. After 650° C./10% H2O/100 h hydrothermal aging, the maximum NO conversion of the catalyst was 65.33%.
A certain volume of palladium nitrate liquid salt was weighed according to a Pd loading amount of 0.4 wt % and mixed well with solid powders of the rare earth manganese-zirconium composite oxide Ce0.20Mn0.20La0.05 Y0.05Zr0.50O1.98N0.02. The resulting mixture was dried at 100° C. for 24 hours, and then subjected to heat treatment at 550° C. for 2 hours, and calcination under H2 for 24 hours, and then subjected to head treatment 550° C. for 2 hours, to give the catalyst Pd (0.4 wt %)/Ce0.20Mn0.20La0.05 Y0.05Zr0.50O1.98N0.02. The noble metal Pd was dispersed at the grain boundary and surface of the rare earth manganese-zirconium composite oxide. The above catalyst was tested for catalytic performance, and the resulting maximum NO conversion was 74.74%, the temperature at which the maximum conversion occurred was 270° C. After 650° C./10% H2O/100 h hydrothermal aging, the maximum NO conversion of the catalyst was 63.16%.
A certain volume of platinum acetate liquid salt was weighed according to a Pt loading amount of 0.4 wt % and mixed well with solid powders of the rare earth manganese-zirconium composite oxide Ce0.20Mn0.20 La0.05 Y0.05Zr0.50O1.98N0.02. The resulting mixture was dried at 90° C. for 20 hours, and then subjected to heat treatment at 550° C. for 6 hours, and calcination under H2 reducing atmosphere at 650° C. for 5 hours, to give the catalyst Pt (0.4 wt %)/Ce0.20Mn0.20La0.05 Y0.05Zr0.50O1.98N0.02. The noble metal Pt was dispersed at the grain boundary and surface of the rare earth manganese-zirconium composite oxide. The above catalyst was tested for catalytic performance, and the resulting maximum NO conversion was 77.78%, the temperature at which the maximum NO conversion occurred was 266° C. After 650° C./10% H2O/100 h hydrothermal aging, the maximum NO conversion of the catalyst was 64.37%.
Certain volumes of liquid salts of platinum nitrate and palladium nitrate were weighed according to a Pt0.5Pd0.5 loading amount of 0.4 wt % and mixed well with solid powders of the rare earth manganese-zirconium composite oxide Ce0.20Mn0.20La0.05 Y0.05Zr0.50O1.90N0.10. The resulting mixture was dried at 100° C. for 12 hours, and then subjected to heat treatment at 450° C. for 6 hours, and calcination under H2 reducing atmosphere at 600° C. for 6 hours, to give the catalyst Pt0.5Pd0.5 (0.4 wt %)/Ce0.20Mn0.20La0.05Y0.05Zr0.5001.90N0.10. The noble metals Pt and Pd were dispersed at the grain boundary and surface of the rare earth manganese-zirconium composite oxide. The above catalyst was tested for catalytic performance, and the resulting maximum NO conversion was 78.13%, the temperature at which the maximum conversion occurred was 261° C. After 650° C./10% H2O/100 h hydrothermal aging, the maximum NO conversion of the catalyst was 68.49%.
Certain volumes of liquid salts of platinum nitrate and palladium nitrate were weighed according to a Pt0.67Pd0.33 loading amount of 0.4 wt % and mixed well with solid powders of the rare earth manganese-zirconium composite oxide Ce0.20Mn0.20La0.05Y0.05Zr0.50O1.98N0.02. The resulting mixture was dried at 100° C. for 20 hours, and then subjected to heat treatment at 450° C. for 6 hours, and calcination under H2 reducing atmosphere at 600° C. for 8 hours, to give the catalyst Pt0.67Pd0.33 (0.4 wt %)/Ce0.20Mn0.20La0.05 Y0.05Zr0.50O1.98N0.02. The noble metals Pt and Pd were dispersed at the grain boundary and surface of the rare earth manganese-zirconium composite oxide. The above catalyst was tested for catalytic performance, and the resulting maximum NO conversion was 80.30%, the temperature at which the maximum conversion occurred was 242° C. After 650° C./10% H2O/100 h hydrothermal aging, the maximum NO conversion of the catalyst was 73.11%.
Certain volumes of liquid salts of platinum nitrate and palladium nitrate were weighed according to a Pt0.67Pd0.33 loading amount of 0.4 wt % and mixed well with solid powders of the rare earth manganese-zirconium composite oxide Ce0.20Mn0.20La0.05 Y0.05Zr0.50O1.98N0.02 with gradient distribution of elements. The resulting mixture was dried at 100° C. for 20 hours, and then subjected to heat treatment at 500° C. for 8 hours, and calcination under H2 reducing atmosphere at 550° C. for 5 hours, to give the catalyst Pt0.67Pd0.33 (0.4 wt %)/Ce0.20Mn0.20La0.05 Y0.05Zr0.50O1.98N0.02. The noble metals Pt and Pd were dispersed at the grain boundary and surface of the rare earth manganese-zirconium composite oxide. The above catalyst was tested for catalytic performance, and the resulting maximum NO conversion was 81.43%, the temperature at which the maximum NO conversion occurred was 236° C. After 650° C./10% H2O/100 h hydrothermal aging, the maximum NO conversion of the catalyst was 76.66%.
Certain volumes of liquid salts of platinum nitrate and palladium nitrate were weighed according to a Pt0.75Pd0.25 loading amount of 0.4 wt % and mixed well with solid powders of the rare earth manganese-zirconium composite oxide Ce0.20Mn0.20La0.05Nd0.05Zr0.50O1.98P0.02. The resulting mixture was dried at 90° C. for 24 hours, and then subjected to heat treatment at 450° C. for 6 hours, and calcination under H2 reducing atmosphere at 600° C. for 8 hours, to give the catalyst Pt0.75Pd0.25 (0.4 wt %)/Ce0.20Mn0.20La0.05Nd0.05Zr0.50O1.98P0.02. The noble metals Pt and Pd were dispersed at the grain boundary and surface of the rare earth manganese-zirconium composite oxide. The above catalyst was tested for catalytic performance, and the resulting maximum NO conversion was 79.38%, the temperature at which the maximum NO conversion occurred was 253° C. After 650° C./10% H2O/100 h hydrothermal aging, the maximum NO conversion of the catalyst was 70.16%.
Certain volumes of liquid salts of platinum nitrate and palladium nitrate were weighed according to a Pt0.91Pd0.09 loading amount of 0.4 wt % and mixed well with solid powders of the rare earth manganese-zirconium composite oxide Ce0.14Mn0.16La0.03Nd0.04 Y0.05Zr0.58O2. The resulting mixture was dried at 120° C. for 6 hours, and then subjected to heat treatment at 450° C. for 6 hours, and calcination under H2 reducing atmosphere at 600° C. for 8 hours, to give the catalyst Pt0.91Pd0.09 (0.4 wt %)/Ce0.14Mn0.16La0.03Nd0.04 Y0.05Zr0.58O2. The noble metals Pt and Pd were dispersed at the grain boundary and surface of the rare earth manganese-zirconium composite oxide. The above catalyst was tested for catalytic performance, and the resulting maximum NO conversion was 80.63%, the temperature at which the maximum NO conversion occurred was 241° C. After 650° C./10% H2O/100 h hydrothermal aging, the maximum NO conversion of the catalyst was 74.36%.
Certain volumes of liquid salts of platinum nitrate and palladium nitrate were weighed according to a Pt0.83Pd0.17 loading amount of 0.4 wt % and mixed well with solid powders of the rare earth manganese-zirconium composite oxide Ce0.20Mn0.20La0.05 Y0.05Zr0.50O1.98F0.02. The resulting mixture was dried at 80° C. for 24 hours, and then subjected to heat treatment at 450° C. for 6 hours, and calcination under H2 reducing atmosphere at 600° C. for 8 hours, to give the catalyst Pt0.83Pd0.17 (0.4 wt %)/Ce0.20Mn0.20La0.05 Y0.05Zr0.50O1.98F0.02. The noble metals Pt and Pd were dispersed at the grain boundary and surface of the rare earth manganese-zirconium composite oxide. The above catalyst was tested for catalytic performance, and the resulting maximum NO conversion was 79.43%, the temperature at which the maximum NO conversion occurred was 246° C. After 650° C./10% H2O/100 h hydrothermal aging, the maximum NO conversion of the catalyst was 71.67%.
Certain volumes of liquid salts of platinum nitrate and palladium nitrate were weighed according to a Pt0.91Pd0.09 loading amount of 0.4 wt % and mixed well with solid powders of the rare earth manganese-zirconium composite oxide Ce0.20Mn0.20La0.02Nd0.03 Y0.03Cu0.02Zr0.50O1.98. The resulting mixture was dried at 150° C. for 10 hours, and then subjected to heat treatment at 450° C. for 6 hours, and calcination under H2 reducing atmosphere at 600° C. for 8 hours, to give the catalyst Pt0.91Pd0.09 (0.4 wt %)/Ce0.20Mn0.20La0.02Nd0.03 Y0.03Cu0.02Zr0.50O1.98. The noble metals Pt and Pd were dispersed at the grain boundary and surface of the rare earth manganese-zirconium composite oxide. The above catalyst was tested for catalytic performance, and the resulting maximum NO conversion was 82.39%, the temperature at which the maximum NO conversion occurred was 236° C. After 650° C./10% H2O/100 h hydrothermal aging, the maximum NO conversion of the catalyst was 76.88%.
Certain volumes of liquid salts of platinum nitrate and palladium nitrate were weighed according to a Pt0.91Pd0.09 loading amount of 0.4 wt % and mixed well with solid powders of the rare earth manganese-zirconium composite oxide Ce0.14Mn0.16La0.03 Nd0.04Y0.05Zr0.58O2 having a core-shell structure. The resulting mixture was dried at 110° C. for 7 hours, and then subjected to heat treatment at 460° C. for 5 hours, and calcination under H2 reducing atmosphere at 550° C. for 5 hours, to give the catalyst Pt0.91Pd0.09 (0.4 wt %)/Ce0.14Mn0.16La0.03Nd0.04 Y0.05Zr0.58O2. The noble metals Pt and Pd were dispersed at the grain boundary and surface of the rare earth manganese-zirconium composite oxide. The above catalyst was tested for catalytic performance, and the resulting maximum NO conversion was 81.98%, the temperature at which the maximum NO conversion occurred was 234° C. After 650° C./10% H2O/100 h hydrothermal aging, the maximum NO conversion of the catalyst was 77.33%.
A certain amount of catalyst Pt0.91Pd0.09 (0.4 wt %)/Ce0.20Mn0.20La0.02Nd0.03 Y0.03Cu0.02Zr0.50O1.98 prepared in Example 15 was taken and prepared to a slurry by mixing with an adhesive, an acidity regulator, and water. The slurry was coated onto a cordierite ceramic honeycomb carrier. The coated carrier was dried at 100° C. for 4 hours, and then subjected to calcination under air atmosphere at 550° C. for 5 hours to give the honeycomb noble metal catalyst Pt0.91Pd0.09 (0.35 g/L)/Ce0.20Mn0.20La0.02Nd0.03Y0.03Cu0.02 Zr0.50O1.99 with the noble metals Pt and Pd dispersed at the grain boundary and surface of the rare-earth manganese-zirconium composite oxide. The above catalyst was tested for catalytic performance, and the resulting maximum NO conversion was 83.86%, the temperature at which the maximum NO conversion occurred was 230° C. After 650° C./10% H2O/100 h hydrothermal aging, the maximum NO conversion of the catalyst was 75.1%.
A certain volume of platinum nitrate liquid salt was weighed according to a Pt loading amount of 0.6 wt % and mixed well with solid powders of the rare earth manganese-zirconium composite oxide Ce0.20Mn0.20La0.02Nd0.03 Sm0.03Y0.02Zr0.50O1.98. The resulting mixture was dried at 60° C. for 32 hours, and then subjected to heat treatment at 400° C. for 9 hours, and calcination under H2 reducing atmosphere at 550° C. for 9 hours, to give the catalyst Pt (0.6 wt %)/Ce0.20Mn0.20La0.02Nd0.03 Sm0.03Y0.02Zr0.50O1.98. The noble metal Pt was dispersed at the grain boundary and surface of the rare earth manganese-zirconium composite oxide. The above catalyst was tested for catalytic performance, and the resulting maximum NO conversion was 80.36%, the temperature at which the maximum NO conversion occurred was 245° C. After 650° C./10% H2O/100 h hydrothermal aging, the maximum NO conversion of the catalyst was 70.43%.
A certain volume of platinum nitrate liquid salt was weighed according to a Pt loading amount of 0.8 wt % and mixed well with solid powders of the rare earth manganese-zirconium composite oxide Ce0.20Mn0.30La0.02Co0.03Y0.05Zr0.40O1.98. The resulting mixture was dried at 100° C. for 6 hours, and then subjected to heat treatment at 400° C. for 9 hours, and calcination under H2 reducing atmosphere 550° C. for 12 at hours, to give the catalyst Pt (0.8 wt %)/Ce0.20Mn0.30La0.02Co0.03Y0.05Zr0.40O1.98. The noble metal Pt was dispersed at the grain boundary and surface of the rare earth manganese-zirconium composite oxide. The above catalyst was tested for catalytic performance, and the resulting maximum NO conversion was 78.36%, the temperature at which the maximum NO conversion occurred was 246° C. After 650° C./10% H2O/100 h hydrothermal aging, the maximum NO conversion of the catalyst was 68.41%.
A certain volume of ruthenium nitrate liquid salt was weighed according to a Ru loading amount of 0.1 wt % and mixed well with solid powders of the rare earth manganese-zirconium composite oxide Ce0.40Mn0.05La0.05Sr0.05Sc0.05Zr0.40O1.98. The resulting mixture was dried at 80° C. for 30 hours, and then subjected to heat treatment at 700° C. for 1 hour, and calcination under CO reducing atmosphere at 750° C. for 9 hours, to give the catalyst Ru (0.1 wt %)/Ce0.40Mn0.05La0.05Sr0.05Sc0.05Zr0.40O1.98. The noble metal Ru was dispersed at the grain boundary and surface of the rare earth manganese-zirconium composite oxide. The above catalyst was tested for catalytic performance, and the resulting maximum NO conversion was 69.16%, the temperature at which the maximum NO conversion occurred was 276° C. After 650° C./10% H2O/100 h hydrothermal aging, the maximum NO conversion of the catalyst was 59.38%.
A certain volume of ruthenium nitrate liquid salt was weighed according to a Ru loading amount of 0.1 wt % and mixed well with solid powders of the rare earth manganese-zirconium composite oxide Ce0.40Mn0.05La0.05Sr0.05Sc0.05Zr0.40O1.98. The resulting mixture was dried at 90° C. for 15 hours, and then subjected to heat treatment at a low temperature of 300° C. for 4 hours, another heat treatment at a high temperature of 700° C. for 3 hours, and calcination under CO reducing atmosphere at 750° C. for 6 hours, to give the catalyst Ru (0.1 wt %)/Ce0.40Mn0.05La0.05 Sr0.05Sc0.05Zr0.40O1.98. The noble metal Ru was dispersed at the grain boundary and surface of the rare earth manganese-zirconium composite oxide. The above catalyst was tested for catalytic performance, and the resulting maximum NO conversion was 70.02%, the temperature at which the maximum NO conversion occurred was 271° C. After 650° C./10% H2O/100 h hydrothermal aging, the maximum NO conversion of the catalyst was 60.16%.
A certain volume of iridium nitrate liquid salt was weighed according to an Ir loading amount of 0.1 wt % and mixed well with solid powders of Ce0.40Mn0.05La0.05Ba0.05Al0.05Zr0.40O1.98. The resulting mixture was dried at 120° C. for 5 hours, and then subjected to heat treatment at 600° C. for 9 hours, and calcination under H2 reducing atmosphere at 750° C. for 6 hours, to give the catalyst Ir (0.1 wt %)/Ce0.40Mn0.05La0.05Ba0.05Al0.05Zr0.40O1.98. The noble metal Ir was dispersed at the grain boundary and surface of the rare earth manganese-zirconium composite oxide. The above catalyst was tested for catalytic performance, and the resulting maximum NO conversion was 68.11%, the temperature at which the maximum NO conversion occurred was 279° C. After 650° C./10% H2O/100 h hydrothermal aging, the maximum NO conversion of the catalyst was 56.9%.
A certain volume of osmium acetate liquid salt was weighed according to an Os loading amount of 0.01 wt % and mixed well with solid powders of Ce0.40Mn0.05La0.05Hf0.05Ni0.05Zr0.40O1.98. The resulting mixture was dried at 160° C. for 1 hour, and then subjected to heat treatment at 750° C. for 0.5 hours, and calcination under H2 reducing atmosphere at 800° C. for 1 hour, to give the catalyst Os (0.01 wt %)/Ce0.40Mn0.05La0.05Hf0.05Ni0.05Zr0.40O1.98. The noble metal Os was dispersed at the grain boundary and surface of the rare earth manganese-zirconium composite oxide. The above catalyst was tested for catalytic performance, and the resulting maximum NO conversion was 66.39%, the temperature at which the maximum NO conversion occurred was 286° C. After 650° C./10% H2O/100 h hydrothermal aging, the maximum NO conversion of the catalyst was 53.83%.
A certain volume of platinum nitrate liquid salt was weighed according to a Pt loading amount of 0.8 wt % and mixed well with solid powders of 30 g of Ce0.20Mn0.30 La0.05 Y0.05Zr0.40O1.98 and 70 g of alumina. The resulting mixture was dried at 90° C. for 6 hours, and then subjected to heat treatment at 400° C. for 9 hours, and calcination under H2 reducing atmosphere at 550° C. for 9 hours, to give the catalyst Pt (0.8 wt %)/Ce0.20Mn0.30La0.05Y0.05Zr0.40O1.98—Al2O3. The noble metal Pt was dispersed at the grain boundary and surface of the rare earth manganese-zirconium composite oxide and alumina. The above catalyst was tested for catalytic performance, and the resulting maximum NO conversion was 79.93%, the temperature at which the maximum NO conversion occurred was 243° C. After 650° C./10% H2O/100 h hydrothermal aging, the maximum NO conversion of the catalyst was 70.53%.
A certain amount of catalyst Pt (0.8 wt %)/Ce0.20Mn0.30La0.05 Y0.05 Zr0.40O1.98—Al2O3 prepared in Example 22 was taken to prepare a slurry by mixing with an adhesive, an acidity regulator, water, and the like. The prepared slurry was coated onto a cordierite ceramic honeycomb carrier. The coated honeycomb carrier was dried at 100° C. for 4 hours, and then subjected to calcination under air atmosphere at 600° C. for 1 hour to give the honeycomb noble metal catalyst Pt (0.5 g/L)/Ce0.20Mn0.30La0.05 Y0.05 Zr0.40O1.98—Al2O3 with the noble metal Pt dispersed at the grain boundary and surface of the rare-earth manganese-zirconium composite oxide and alumina. The above catalyst was tested for catalytic performance, and the resulting maximum NO conversion was 81.69%, the temperature at which the maximum NO conversion occurred was 241° C. After 650° C./10% H2O/100 h hydrothermal aging, the maximum NO conversion of the catalyst was 73.18%.
A certain volume of platinum nitrate liquid salt was weighed according to a Pt loading amount of 1.0 wt % and mixed well with solid powders of 40 g of Ce0.30Mn0.25La0.05Nd0.05W0.05Zr0.3001.98 and 60 g of alumina. The resulting mixture was dried at 130° C. for 2 hours, and then subjected to heat treatment at 450° C. for 12 hours, and calcination under H2 reducing atmosphere at 700° C. for 7 hours, to give the catalyst Pt (1.0 wt %)/Ce0.30Mn0.25La0.05Nd0.05W0.05Zr0.30O1.98—Al2O3. The noble metal Pt was dispersed at the grain boundary and surface of the rare earth manganese-zirconium composite oxide and alumina. The above catalyst was tested for catalytic performance, and the resulting maximum NO conversion was 78.61%, the temperature at which the maximum NO conversion occurred was 253° C. After 650° C./10% H2O/100 h hydrothermal aging, the maximum NO conversion of the catalyst was 66.84%.
A certain volume of platinum nitrate liquid salt was weighed according to a Pt loading amount of 1.0 wt % and mixed well with solid powders of 50 g of Ce0.30Mn0.30La0.05Cu0.05Zr0.3001.98 and 50 g of alumina. The resulting mixture was dried at 140° C. for 5 hours, and then subjected to heat treatment at 450° C. for 12 hours, and calcination under H2 reducing atmosphere at 700° C. for 8 hours, to give the catalyst Pt (1.0 wt %)/Ce0.30Mn0.30La0.05Cu0.05Zr0.30O1.98—Al2O3. The noble metal Pt was dispersed at the grain boundary and surface of the rare earth manganese-zirconium composite oxide and alumina. The above catalyst was tested for catalytic performance, and the resulting maximum NO conversion was 77.36%, the temperature at which the maximum NO conversion occurred was 256° C. After 650° C./10% H2O/100 h hydrothermal aging, the maximum NO conversion of the catalyst was 65.18%.
A certain volume of platinum nitrate liquid salt was weighed according to a Pt loading amount of 1.0 wt % and mixed well with solid powders of 60 g of Ce0.30Mn0.10La0.05Nd0.05W0.05Zr0.3001.98 and 40 g of alumina. The resulting mixture was dried at 80° C. for 9 hours, and then subjected to heat treatment at 450° C. for 12 hours, and calcination under H2 reducing atmosphere at 700° C. for 7 hours, to give the catalyst Pt (1.0 wt %)/Ce0.40Mn0.10La0.05Nd0.05 Ti0.20Zr0.20O1.98—Al2O3. The noble metal Pt was dispersed at the grain boundary and surface of the rare earth manganese-zirconium composite oxide and alumina. The above catalyst was tested for catalytic performance, and the resulting maximum NO conversion was 77.7%, the temperature at which the maximum NO conversion occurred was 272° C. After 650° C./10% H2O/100 h hydrothermal aging, the maximum NO conversion of the catalyst was 66.79%.
A certain volume of platinum nitrate liquid salt was weighed according to a Pt loading amount of 2.0 wt % and mixed well with solid powders of 70 g of Ce0.40Mn0.10La0.05Nd0.05V0.20Zr0.20O1.98 and 30 g of alumina. The resulting mixture was dried at 200° C. for 1 hour, and then subjected to heat treatment at 600° C. for 6 hours, and calcination under H2 reducing atmosphere at 700° C. for 9 hours, to give the catalyst Pt (2.0 wt %)/Ce0.40Mn0.10La0.05Nd0.05V0.20Zr0.20O1.98—Al2O3. The noble metal Pt was dispersed at the grain boundary and surface of the rare earth manganese-zirconium composite oxide and alumina. The above catalyst was tested for catalytic performance, and the resulting maximum NO conversion was 78.6%, the temperature at which the maximum NO conversion occurred was 269° C. After 650° C./10% H2O/100 h hydrothermal aging, the maximum NO conversion of the catalyst was 67.46%.
A certain volume of platinum nitrate liquid salt was weighed according to a Pt loading amount of 2.0 wt % and mixed well with solid powders of 30 g of alumina and 70 g of Ce0.40Mn0.10La0.05Nd0.05V0.20Zr0.20O1.98. The resulting mixture was dried at 200° C. for 1 hour, and then subjected to heat treatment at a low temperature of 230° C. for 6 hours, and another heat treatment at a high temperature of 630° C. for 4 hours, and calcination under H2 reducing atmosphere at 700° C. for 5 hours, to give the catalyst Pt (2.0 wt %)/Ce0.40Mn0.10La0.05Nd0.05V0.20Zr0.20O1.98—Al2O3. The noble metal Pt was dispersed at the grain boundary and surface of the rare earth manganese-zirconium composite oxide and alumina. The above catalyst was tested for catalytic performance, and the resulting maximum NO conversion was 79.96%, the temperature at which the maximum NO conversion occurred was 261° C. After 650° C./10% H2O/100 h hydrothermal aging, the maximum NO conversion of the catalyst was 68.41%.
A certain volume of rhodium nitrate liquid salt was weighed according to a Rh loading amount of 0.5 wt % and mixed well with solid powders of 80 g of Ce0.40Mn0.05 La0.05Nd0.05Nb0.05Zr0.40O1.98 and 20 g of alumina. The resulting mixture was dried at 50° C. for 48 hours, and then subjected to heat treatment at 300° C. for 3 hours, and calcination under H2 reducing atmosphere at 850° C. for 0.5 hours, to give the catalyst Rh (0.5 wt %)/Ce0.40Mn0.05La0.05Nd0.05Nb0.05Zr0.40O1.98—Al2O3. The noble metal Rh was dispersed at the grain boundary and surface of the rare earth manganese-zirconium composite oxide and alumina. The above catalyst was tested for catalytic performance, and the resulting maximum NO conversion was 73.43%, the temperature at which the maximum NO conversion occurred was 269° C. After 650° C./10% H2O/100 h hydrothermal aging, the maximum NO conversion of the catalyst was 61.53%.
A certain volume of silver citrate liquid salt was weighed according to an Ag loading amount of 0.5 wt % and mixed well with solid powders of 90 g of Ce0.40Mn0.05La0.05Nd0.05Si0.05Zr0.40O1.98 and 10 g of alumina. The resulting mixture was dried at 160° C. for 4 hours, and then subjected to heat treatment at 600° C. for 9 hours, and calcination under H2 reducing atmosphere at 750° C. for 6 hours, to give the catalyst Ag (0.5 wt %)/Ce0.40Mn0.05La0.05Nd0.05Si0.05Zr0.40O1.98—Al2O3. The noble metal Ag was dispersed at the grain boundary and surface of the rare earth manganese-zirconium composite oxide and alumina. The above catalyst was tested for catalytic performance, and the resulting maximum NO conversion was 70.93%, the temperature at which the maximum NO conversion occurred was 270° C. After 650° C./10% H2O/100 h hydrothermal aging, the maximum NO conversion of the catalyst was 60.37%.
A certain volume of gold chloride liquid salt was weighed according to an Au loading amount of 0.5 wt % and mixed well with solid powders of 90 g of Ce0.40Mn0.05La0.05Nd0.05Fe0.05Zr0.40O1.98 and 10 g of alumina. The resulting mixture was washed and dried at 100° C. for 8 hours, and then subjected to heat treatment at 200° C. for 24 hours, and calcination under H2 reducing atmosphere at 400° C. for 24 hours, to give the catalyst Au (0.5 wt %)/Ce0.40Mn0.05La0.05Nd0.05Fe0.05Zr0.40O1.98—Al2O3. The noble metal Au was dispersed at the grain boundary and surface of the rare earth manganese-zirconium composite oxide and alumina. The above catalyst was tested for catalytic performance, and the resulting maximum NO conversion was 71.34%, the temperature at which the maximum NO conversion occurred was 281° C. After 650° C./10% H2O/100 h hydrothermal aging, the maximum NO conversion of the catalyst was 60.66%.
A certain volume of platinum nitrate liquid salt was weighed according to a Pt loading amount of 1.0 wt % and mixed well with alumina solid powders. The resulting mixture was dried at 50° C. for 6 hours, and then subjected to heat treatment at 450° C. for 12 hours, and calcination under H2 reducing atmosphere at 700° C. for 7 hours, to give the catalyst Pt (1.0 wt %)/Al2O3. The noble metal Pt was dispersed at the grain boundary and surface of alumina. The above catalyst was tested for catalytic performance, and the resulting maximum NO conversion was 70.96%, the temperature at which the maximum NO conversion occurred was 283° C. After 650° C./10% H2O/100 h hydrothermal aging, the maximum NO conversion of the catalyst was 60.31%.
A certain amount of catalyst Pt (1.0 wt %)/Al2O3 prepared in Example 31 was taken to prepare a slurry by mixing well with an adhesive, an acidity regulator, water, and the like. The prepared slurry was coated onto a cordierite ceramic honeycomb carrier. The coated honeycomb carrier was dried at 110° C. for 5 hours, and then subjected to calcination under air atmosphere at 450° C. for 6 hours to give the honeycomb noble metal catalyst Pt (0.03 g/L)/Al2O3 with the noble metal Pt dispersed at the grain boundary and surface of alumina. The above catalyst was tested for catalytic performance, and the resulting maximum NO conversion was 68.33%, the temperature at which the maximum NO conversion occurred was 279° C. After 650° C./10% H2O/100 h hydrothermal aging, the maximum NO conversion of the catalyst was 60.93%.
A certain volume of platinum nitrate liquid salt was weighed according to a Pt loading amount of 0.2 wt % and mixed well with solid powders of Ce0.20Mn0.15Y0.15Zr0.50O1.99. The resulting mixture was dried at 110° C. for 12 hours, and then subjected to heat treatment at 530° C. for 8 hours, and calcination under H2 reducing atmosphere at 650° C. for 3 hours, to give the catalyst Pt (0.2 wt %)/Ce0.20Mn0.15Y0.15Zr0.50O1.99. The noble metal Pt was dispersed at the grain boundary and surface of the rare earth manganese-zirconium composite oxide. The above catalyst was tested for catalytic performance, and the resulting maximum NO conversion was 76.49%, the temperature at which the maximum NO conversion occurred was 270° C. After 650° C./10% H2O/100 h hydrothermal aging, the maximum NO conversion of the catalyst was 63.31%.
A certain amount of catalyst Pt (0.2 wt %)/Ce0.20Mn0.15Y0.15Zr0.50O1.99 prepared in Example 33 was taken to prepare a slurry by mixing well with an adhesive, an acidity regulator, water, and the like. The prepared slurry was coated onto a cordierite ceramic honeycomb carrier. The coated honeycomb carrier was dried at 130° C. for 6 hours, and then subjected to calcination under air atmosphere at 500° C. for 3 hours to give the honeycomb noble metal catalyst Pt (0.15 g/L)/Ce0.20Mn0.15 Y0.15Zr0.50O1.99, with the noble metal Pt dispersed at the grain boundary and surface of the rare earth manganese-zirconium composite oxide. The above catalyst was tested for catalytic performance, and the resulting maximum NO conversion was 76.43%, the temperature at which the maximum NO conversion occurred was 266° C. After 650° C./10% H2O/100 h hydrothermal aging, the maximum NO conversion of the catalyst was 65.13%.
A certain volume of platinum nitrate liquid salt was weighed according to a Pt loading amount of 1.1 g/L and prepared to a slurry by mixing well with Ce0.20Mn0.20 La0.05Nd0.05W0.05Zr0.50O1.98N0.02, an acidity regulator and water before mixing well with an adhesive. The slurry was coated onto a cordierite ceramic honeycomb carrier. The coated carrier was dried at 80° C. for 8 hours and then subjected to heat treatment at a low temperature of 310° C. for 8 hours, another heat treatment at a high temperature of 730° C. for 2 hours, and calcination under H2 reducing atmosphere at 800° C. for 3 hours to give the honeycomb noble metal catalyst Pt (1.1 g/L)/Ce0.20Mn0.20La0.05Nd0.05W0.05Zr0.50O1.98N0.02, with the noble metal Pt dispersed at the grain boundary and surface of the rare earth manganese-zirconium composite oxide. The above catalyst was tested for catalytic performance, and the resulting maximum NO conversion was 77.71%, the temperature at which the maximum NO conversion occurred was 256° C. After 650° C./10% H2O/100 h hydrothermal aging, the maximum NO conversion of the catalyst was 66.73%.
A certain volume of platinum nitrate liquid salt was weighed according to a Pt loading amount of 1.1 g/L and prepared to a slurry by adding Al2O3, Ce0.30Mn0.25La0.05Nd0.05W0.05Zr0.30O1.99, an acidity regulator and water and mixed well before adding an adhesive and mixing well. The slurry was coated onto a cordierite ceramic honeycomb carrier. The coated carrier was dried at 80° C. for 8 hours and then subjected to heat treatment at 400° C. for 8 hours and calcination under H2 reducing atmosphere at 600° C. for 3 hours to give the honeycomb noble metal catalyst Pt (1.1 g/L)/Ce0.30Mn0.25La0.05Nd0.05W0.05Zr0.30O1.99—Al2O3, with the noble metal Pt dispersed at the grain boundary and surface of the rare earth manganese-zirconium composite oxide and alumina. The above catalyst was tested for catalytic performance, and the resulting maximum NO conversion was 79.17%, the temperature at which the maximum NO conversion occurred was 236° C. After 650° C./10% H2O/100 h hydrothermal aging, the maximum NO conversion of the catalyst was 68.37%.
A certain volume of platinum nitrate liquid salt was weighed according to a Pt loading amount of 1.1 g/L and prepared to a slurry by mixing well with Al2O3, Ce0.30Mn0.25 La0.05Nd0.05 Y0.05Zr0.30O1.99 having gradient distribution of elements, an acidity regulator and water before mixing well an adhesive. The slurry was coated onto a cordierite ceramic honeycomb carrier. The coated carrier was dried at 80° C. for 8 hours and then subjected to heat treatment at 500° C. for 8 hours and calcination under H2 reducing atmosphere at 550° C. for 5 hours to give the honeycomb noble metal catalyst Pt (1.1 g/L)/Ce0.30Mn0.25La0.05Nd0.05Y0.05Zr0.30O1.99—Al2O3, with the noble metal Pt dispersed at the grain boundary and surface of the rare earth manganese-zirconium composite oxide and alumina. The above catalyst was tested for catalytic performance, and the resulting maximum NO conversion was 80.11%, the temperature at which the maximum NO conversion occurred was 234° C. After 650° C./10% H2O/100 h hydrothermal aging, the maximum NO conversion of the catalyst was 69.83%.
A certain volume of platinum nitrate liquid salt was weighed according to a Pt loading amount of 1.5 g/L and prepared to a slurry by mixing well with Al2O3, an acidity regulator and water, etc. before mixing well with an adhesive. The slurry was coated onto a cordierite ceramic honeycomb carrier. The coated carrier was dried at 150° C. for 3 hours and then subjected to heat treatment at 500° C. for 6 hours and calcination under H2 reducing atmosphere at 550° C. for 2 hours to give the honeycomb noble metal catalyst Pt (1.5 g/L)/Al2O3, with the noble metal Pt dispersed at the grain boundary and surface of alumina. The above catalyst was tested for catalytic performance, and the resulting maximum NO conversion was 72.36%, the temperature at which the maximum NO conversion occurred was 266° C. After 650° C./10% H2O/100 h hydrothermal aging, the maximum NO conversion of the catalyst was 62.11%.
A certain volume of platinum nitrate liquid salt was weighed according to a Pt loading amount of 2.0 g/L and prepared to a slurry by mixing well with Ce0.40Mn0.10La0.05Nd0.05V0.20Zr0.20O1.98, an acidity regulator, water, etc. before mixing well with an adhesive. The slurry was coated onto a cordierite ceramic honeycomb carrier. The coated carrier was dried at 100° C. for 4 hours and then subjected to heat treatment at 380° C. for 7 hours and calcination under H2 reducing atmosphere at 500° C. for 4 hours. Then Al2O3, an adhesive, an acidity regulator and water, etc. were mixed to prepare a slurry. The slurry was coated onto the above calcined cordierite ceramic honeycomb carrier, which was then dried at 90° C. for 3 hours and subjected to calcination at 450° C. for 8 hours to give the honeycomb noble metal catalyst Pt (2.0 g/L)/Ce0.40Mn0.10La0.05Nd0.05V0.20Zr0.20O1.98—Al2O3, with the noble metal Pt dispersed at the grain boundary and surface of the rare earth manganese-zirconium composite oxide. The above catalyst was tested for catalytic performance, and the resulting maximum NO conversion was 81.19%, the temperature at which the maximum NO conversion occurred was 239° C. After 650° C./10% H2O/100 h hydrothermal aging, the maximum NO conversion of the catalyst was 70.19%.
A certain volume of platinum nitrate liquid salt was weighed according to a Pt loading amount of 1.3 g/L and prepared to a slurry by mixing well with Al2O3, an acidity regulator, water, etc. before mixing well with an adhesive. The slurry was coated onto a cordierite ceramic honeycomb carrier. The coated carrier was dried at 120° C. for 4 hours and then subjected to heat treatment at 430° C. for 5 hours and calcination under H2 reducing atmosphere at 500° C. for 7 hours. Then Ce0.30Mn0.30La0.05Cu0.05Zr0.30O1.98, an adhesive, an acidity regulator and water, etc. were mixed to prepare a slurry. The slurry was coated onto the above calcined cordierite ceramic honeycomb carrier, which was then dried at 90° C. for 3 hours and subjected to calcination under air atmosphere at 450° C. for 2 hours to give the honeycomb noble metal catalyst Pt (1.3 g/L)/Ce0.30Mn0.30La0.05Cu0.05Zr0.30O1.98—Al2O3, with the noble metal Pt dispersed at the grain boundary and surface of alumina. The above catalyst was tested for catalytic performance, and the resulting maximum NO conversion was 80.60%, the temperature at which the maximum NO conversion occurred was 233° C. After 650° C./10% H2O/100 h hydrothermal aging, the maximum NO conversion of the catalyst was 69.33%.
A certain volume of platinum nitrate liquid salt was weighed according to a Pt loading amount of 1.5 g/L and prepared to a slurry by mixing well with Al2O3, an acidity regulator, water, etc. before mixing well with an adhesive. The slurry was coated onto a cordierite ceramic honeycomb carrier. The coated carrier was dried at 90° C. for 3 hours and then subjected to heat treatment at a low temperature of 340° C. for 5 hours, another heat treatment at a high temperature of 560° C. for 3 hours, and calcination under H2 reducing atmosphere at 650° C. for 5 hours. Then Ce0.40Mn0.05La0.05Nd0.05Fe0.05Zr0.40O1.98, an adhesive, an acidity regulator and water, etc. were mixed to prepare a slurry. The slurry was coated onto the above calcined cordierite ceramic honeycomb carrier, which was then dried at 100° C. for 5 hours and subjected to calcination under air atmosphere at 510° C. for 2 hours to give the honeycomb noble metal catalyst Pt (1.5 g/L)/Ce0.40Mn0.05La0.05Nd0.05Fe0.05Zr0.40O1.98—Al2O3, with the noble metal Pt dispersed at the grain boundary and surface of alumina. The above catalyst was tested for catalytic performance, and the resulting maximum NO conversion was 79.60%, the temperature at which the maximum NO conversion occurred was 243° C. After 650° C./10% H2O/100 h hydrothermal aging, the maximum NO conversion of the catalyst was 69.81%.
A certain volume of platinum nitrate liquid salt was weighed according to a Pt loading amount of 2.0 g/L. Half of the platinum nitrate liquid salt was mixed well with an appropriate amount of Ce0.40Mn0.10La0.05Nd0.05V0.20Zr0.20O1.98, an acidity regulator, water, etc. and then mixed well with an adhesive to prepare a coating slurry. The slurry was coated onto a cordierite ceramic honeycomb carrier. The coated carrier was dried at 110° C. for 6 hours and subjected to heat treatment at 500° C. for 6 hours and calcination under H2 reducing atmosphere at 700° C. for 3 hours. The rest half of the platinum nitrate liquid salt was mixed well with an appropriate amount of Al2O3 powders, an acidity regulator, water, etc. and then mixed well with an adhesive to prepare a coating slurry. The slurry was coated onto the above calcined cordierite ceramic honeycomb carrier. The resulting carrier was dried at 90° C. for 3 hours and subjected to heat treatment at 560° C. for 4 hours and calcination under H2 reducing atmosphere at 500° C. for 7 hours to give the honeycomb noble metal catalyst Pt (2.0 g/L)/Ce0.40Mn0.10La0.05Nd0.05V0.20Zr0.20O1.98—Al2O3, with the noble metal Pt dispersed at the grain boundary and surface of the rare earth manganese-zirconium composite oxide and alumina. The above catalyst was tested for catalytic performance, and the resulting maximum NO conversion was 82.96%, the temperature at which the maximum NO conversion occurred was 236° C. After 650° C./10% H2O/100 h hydrothermal aging, the maximum NO conversion of the catalyst was 70.16%.
A certain volume of platinum nitrate liquid salt was weighed according to a Pt loading amount of 1.0 g/L and prepared to a slurry by mixing well with 20 g of Ce0.40Mn0.10La0.05Nd0.05Pr0.20Zr0.20O1.98, 70 g of alumina, an acidity regulator, water, etc. before mixing well with an adhesive. The slurry was coated onto a cordierite ceramic honeycomb carrier. The coated carrier was dried at 80° C. for 13 hours and then subjected to heat treatment at 330° C. for 8 hours and calcination under H2 reducing atmosphere at 550° C. for 4 hours. Then 10 g of alumina was weighed and prepared to a slurry by mixing well with an adhesive, an acidity regulator and water, etc. The slurry was coated onto the above calcined cordierite ceramic honeycomb carrier, which was then dried at 90° C. for 3 hours and subjected to calcination at 600° C. for 1 hour to give the honeycomb noble metal catalyst Pt (1.0 g/L)/Ce0.40Mn0.10La0.05Nd0.05Pr0.20Zr0.20O1.98—Al2O3, with the noble metal Pt dispersed at the grain boundary and surface of the rare earth manganese-zirconium composite oxide and alumina. The above catalyst was tested for catalytic performance, and the resulting maximum NO conversion was 79.31%, the temperature at which the maximum NO conversion occurred was 256° C. After 650° C./10% H2O/100 h hydrothermal aging, the maximum NO conversion of the catalyst was 68.69%.
40 g of Al2O3 was weighed and mixed well with an acidity regulator, an adhesive, and water to prepare a slurry. The prepared slurry was coated onto a cordierite ceramic honeycomb carrier. The coated carrier was dried at 120° C. for 4 hours and then subjected to calcination under air atmosphere at 500° C. for 7 hours. A certain volume of platinum nitrate liquid salt was weighed according to a Pt loading amount of 1.4 g/L and prepared to a slurry by mixing well with 40 g of Ce0.30Mn0.20La0.10Cu0.10Zr0.30O1.98, 20 g of Al2O3, an acidity regulator, water, etc. before mixing well with an adhesive. The resulting slurry was coated onto the above calcined cordierite ceramic honeycomb carrier. The resulting carrier was dried at 90° C. for 3 hours and then subjected to heat treatment at 430° C. for 5 hours and calcination under H2 reducing atmosphere at 550° C. for 3 hours to give the honeycomb noble metal catalyst Pt (1.4 g/L)/Ce0.30Mn0.20La0.10Cu0.10Zr0.30O1.98—Al2O3, with the noble metal Pt dispersed at the grain boundary and surface of the rare earth manganese-zirconium composite oxide and alumina. The above catalyst was tested for catalytic performance, and the resulting maximum NO conversion was 79.33%, the temperature at which the maximum NO conversion occurred was 238° C. After 650° C./10% H2O/100 h hydrothermal aging, the maximum NO conversion of the catalyst was 68.16%.
A certain volume of platinum nitrate liquid salt was weighed according to a Pt loading amount of 1.0 g/L and mixed well with 50 g of alumina solid powders, an acidity regulator, an adhesive, water, etc. to prepare a slurry. The prepared slurry was coated onto a cordierite ceramic honeycomb carrier. The coated carrier was dried at 90° C. for 8 hours and then subjected to heat treatment at 460° C. for 5 hours and calcination under H2 reducing atmosphere at 550° C. for 9 hours. 50 g of Ce0.14Mn0.16La0.03Nd0.04 Y0.05Zr0.58O2 with a core-shell structure was weighed and mixed well with an adhesive, an acidity regulator, water, etc. to prepare a slurry. The prepared slurry was coated onto the above calcined cordierite ceramic honeycomb carrier. The resulting carrier was dried at 80° C. for 8 hours and calcination under H2 reducing atmosphere at 460° C. for 6 hours to give the honeycomb noble metal catalyst Pt (1.0 g/L)/Ce0.14Mn0.16La0.03Nd0.04Y0.05Zr0.58O2—Al2O3. The noble metal Pt was dispersed at the grain boundary and surface of alumina The above catalyst was tested for catalytic performance, and the resulting maximum NO conversion was 81.96%, the temperature at which the maximum NO conversion occurred was 246° C. After 650° C./10% H2O/100 h hydrothermal aging, the maximum NO conversion of the catalyst was 70.19%.
A certain volume of platinum nitrate liquid salt was weighed according to a Pt loading amount of 1.0 wt % and mixed well with 40 g of solid powders of Ce0.20Mn0.25La0.05 Y0.05Fe0.05Zr0.40O1.98. The resulting mixture was dried at 80° C. for 9 hours, and then subjected to heat treatment at 410° C. for 6 hours, and calcination under H2 reducing atmosphere at 560° C. for 7 hours, to give the catalyst Pt (1.0 wt %)/Ce0.20Mn0.25La0.05Y0.05Fe0.05Zr0.40O1.9. The above catalyst was mixed well with an acidity regulator, an adhesive, water, etc. to prepare a slurry. The prepared slurry was coated onto a cordierite ceramic honeycomb carrier. The coated honeycomb carrier was dried at 130° C. for 1 hour and then subjected to calcination under air atmosphere at 400° C. for 6 hours. 60 g of alumina was weighed and mixed well with an adhesive, an acidity regulator, water, etc. to prepare a slurry. The slurry was coated onto the calcined cordierite ceramic honeycomb carrier. The resulting carrier was then dried at 90° C. for 3 hours, and subjected to calcination under air atmosphere at 550° C. for 1 hour to give the honeycomb noble metal catalyst Pt (1.6 g/L)/Ce0.20Mn0.25La0.05 Y0.05Fe0.05Zr0.40O1.98—Al2O3. The noble metal Pt was dispersed at the grain boundary and surface of the rare earth manganese-zirconium composite oxide. The above honeycomb noble metal catalyst was tested for catalytic performance, and the resulting maximum NO conversion was 78.53%, the temperature at which the maximum NO conversion occurred was 249° C. After 650° C./10% H2O/100 h hydrothermal aging, the maximum NO conversion of the catalyst was 69.83%.
A certain amount of Al2O3 was weighed and mixed well with an acidity regulator, an adhesive, and water to prepare a slurry. The prepared slurry was coated onto a cordierite ceramic honeycomb carrier. The coated carrier was dried at 140° C. for 3 hours and then subjected to calcination under air atmosphere at 600° C. for 8 hours. A certain amount of catalyst Pt (1.0 wt %)/Ce0.20Mn0.25La0.05 Y0.05Fe0.05Zr0.40O1.9 prepared according to Example 44 was weighed and mixed well with an adhesive, an acidity regulator, and water to prepare a slurry. The slurry was coated onto the calcined cordierite ceramic honeycomb carrier. The resulting carrier was dried at 90° C. for 3 hours and then subjected to calcination at 330° C. for 6 hours to give the honeycomb noble metal catalyst Pt (1.0 g/L)/Ce0.20Mn0.25La0.05 Y0.05Fe0.05Zr0.40O1.9—Al2O3, with the noble metal Pt dispersed at the grain boundary and surface of the rare earth manganese-zirconium composite oxide. The above catalyst was tested for catalytic performance, and the resulting maximum NO conversion was 79.19%, the temperature at which the maximum NO conversion occurred was 239° C. After 650° C./10% H2O/100 h hydrothermal aging, the maximum NO conversion of the catalyst was 70.37%.
A certain volume of platinum nitrate liquid salt was weighed according to a Pt loading amount of 0.7 wt % and mixed well with alumina solid powders. The resulting mixture was dried at 70° C. for 11 hours, and then subjected to heat treatment at 460° C. for 5 hours, and calcination under H2 reducing atmosphere at 550° C. for 9 hours, to give the catalyst Pt (0.7 wt %)/Al2O3. The above catalyst was mixed well with an acidity regulator, an adhesive, water, etc. to prepare a slurry. The prepared slurry was coated onto a cordierite ceramic honeycomb carrier. The coated honeycomb carrier was dried at 130° C. for 1 hour and then subjected to calcination under air atmosphere at 400° C. for 6 hours. 60 g of Ce0.20Mn0.20La0.05 Y0.05Zn0.10Zr0.40O1.98 was weighed and mixed well with an adhesive, an acidity regulator, water, etc. to prepare a slurry. The slurry was coated onto the calcined cordierite ceramic honeycomb carrier. The coated carrier was then dried at 80° C. for 8 hours, and subjected to calcination under air atmosphere at 460° C. for 6 hours to give the honeycomb noble metal catalyst Pt (1.0 g/L)/Ce0.20Mn0.20La0.05Y0.05Zn0.10Zr0.40O1.98—Al2O3. The noble metal Pt was dispersed at the grain boundary and surface of alumina. The above catalyst was tested for catalytic performance, and the resulting maximum NO conversion was 76.10%, the temperature at which the maximum NO conversion occurred was 266° C. After 650° C./10% H2O/100 h hydrothermal aging, the maximum NO conversion of the catalyst was 67.83%.
A certain volume of platinum acetate liquid salt was weighed according to a Pt loading amount of 1.0 g/L and mixed well with 50 g of alumina solid powders, an acidity regulator, an adhesive, water, etc. to prepare a slurry. The prepared slurry was coated onto the first half of a cordierite ceramic honeycomb carrier. The coated carrier was dried at 100° C. for 6 hours and then subjected to heat treatment at 400° C. for 6 hours and calcination under H2 reducing atmosphere at 550° C. for 7 hours. Then 50 g of Ce0.14Mn0.16 La0.03 Nd0.0+Y0.05Zr0.58O2 was weighed and mixed well with an acidity regulator, an adhesive, water, etc. to prepare a slurry. The prepared slurry was coated onto the second half of the cordierite ceramic honeycomb carrier. The coated carrier was dried at 150° C. for 2 hours and then subjected to calcination at 610° C. for 5 hours to give the honeycomb noble metal catalyst Pt (1.0 g/L)/Ce0.14Mn0.16La0.03 Nd0.04 Y0.05Zr0.58O2—Al2O3, with the noble metal Pt dispersed at the grain boundary and surface of alumina. The above honeycomb noble metal catalyst was tested for catalytic performance, and the resulting maximum NO conversion was 79.13%, the temperature at which the maximum NO conversion occurred was 249° C. After 650° C./10% H2O/100 h hydrothermal aging, the maximum NO conversion of the catalyst was 69.38%.
A certain volume of platinum nitrate liquid salt was weighed according to a Pt loading amount of 0.7 g/L and mixed well with solid powders of Ce0.20Mn0.15 Y0.10Eu0.05Zr0.50O1.99, an acidity regulator, water, etc. before adding an adhesive to prepare a slurry. The prepared slurry was coated onto the first half of a cordierite ceramic honeycomb carrier. The carrier was dried at 100° C. for 6 hours. Then an appropriate amount of alumina was mixed well with an acidity regulator, an adhesive, water, etc. to prepare a slurry. The prepared slurry was coated onto the remaining second half of the cordierite ceramic honeycomb carrier. The resulting carrier was dried at 150° C. for 2 hours and then subjected to calcination at 610° C. for 5 hours to give the honeycomb noble metal catalyst Pt (0.7 g/L)/Ce0.20Mn0.15Y0.10Eu0.05Zr0.50O1.99—Al2O3, with the noble metal Pt dispersed at the grain boundary and surface of the rare earth manganese-zirconium composite oxide. The above honeycomb noble metal catalyst was tested for catalytic performance, and the resulting maximum NO conversion was 77.71%, the temperature at which the maximum NO conversion occurred was 266° C. After 650° C./10% H2O/100 h hydrothermal aging, the maximum NO conversion of the catalyst was 64.93%.
A certain volume of platinum nitrate liquid salt was weighed according to a Pt loading amount of 1.5 g/L and mixed well with a certain amount of alumina, an acidity regulator, water, etc. before adding an adhesive to prepare a slurry. The prepared slurry was coated onto the first half of a cordierite ceramic honeycomb carrier. The coated carrier was dried at 80° C. for 9 hours, and subjected to heat treatment at 380° C. for 6 hours, and calcination under H2 reducing atmosphere at 610° C. for 6 hours. Then a certain amount of Ce0.40Mn0.10La0.05Nd0.05W0.20Zr0.20O1.98 was weighed and mixed well with an adhesive, an acidity regulator, water, etc. to prepare a slurry. The slurry was coated onto the remaining second half of the cordierite ceramic honeycomb carrier. The resulting carrier was dried at 150° C. for 3 hours and then subjected to calcination at 460° C. for 3 hours to give the honeycomb noble metal catalyst Pt (1.5 g/L)/Ce0.40Mn0.10La0.05Nd0.05W0.20Zr0.20O1.98—Al2O3, with the noble metal Pt dispersed at the grain boundary and surface of the rare earth manganese-zirconium composite oxide. The above catalyst was tested for catalytic performance, and the resulting maximum NO conversion was 81.79%, the temperature at which the maximum NO conversion occurred was 246° C. After 650° C./10% H2O/100 h hydrothermal aging, the maximum NO conversion of the catalyst was 71.51%.
A certain volume of platinum nitrate liquid salt was weighed according to a Pt loading amount of 1.3 g/L. Half of the platinum nitrate liquid salt was mixed well with Ce0.40Mn0.10La0.05Nd0.05Pr0.20Zr0.20O1.98, an acidity regulator, water, etc. before mixing well with an adhesive to prepare a coating slurry. The slurry was coated onto the first half of a cordierite ceramic honeycomb carrier. The coated carrier was dried at 80° C. for 9 hours and subjected to heat treatment at 380° C. for 6 hours and calcination under H2 reducing atmosphere at 610° C. for 6 hours. The rest half of the platinum nitrate liquid salt was mixed well with alumina, an acidity regulator, water, etc. before mixing well with an adhesive to prepare a slurry, which was coated onto the remaining half of the cordierite ceramic honeycomb carrier. The resulting carrier was dried at 150° C. for 3 hours and subjected to heat treatment at 460° C. for 6 hours and calcination under H2 reducing atmosphere at 600° C. for 5 hours to give the honeycomb noble metal catalyst Pt (1.3 g/L)/Ce0.40Mn0.10La0.05Nd0.05Pr0.20Zr0.20O1.98—Al2O3, with the noble metal Pt dispersed at the grain boundary and surface of the rare earth manganese-zirconium composite oxide and alumina. The above catalyst was tested for catalytic performance, and the resulting maximum NO conversion was 80.16%, the temperature at which the maximum NO conversion occurred was 251° C. After 650° C./10% H2O/100 h hydrothermal aging, the maximum NO conversion of the catalyst was 70.09%. The above test process involves sampling an appropriate amount of grain boundary and surface-loaded noble metal catalyst and a cut sample of honeycomb noble metal catalyst for testing their catalytic performances, respectively. The catalyst activity evaluation test was performed in a microreactor, and the contents of NO, NO2 and NOx at the corresponding temperatures were recorded by an infrared gas analyzer, so as to calculate the maximum NO conversion of each fresh catalyst sample and the corresponding temperature, as well as the maximum NO conversion after hydrothermal aging at 650° C./10% H2O/100 h. The catalytic test used a simulated automobile exhaust gas mixture with the following content of each component (volume percentage): 8% oxygen, 10% water, 500 ppm carbon monoxide, 500 ppm nitric oxide, 200 ppm C3H6, 100 ppm C3H8; the balance gas being nitrogen. Reaction temperature setting: from room temperature to 400° C. at a rate of 20° C./min for a reaction time of 20 min.
As can be seen from the above experimental results, using the grain boundary and surface-loaded noble metal catalyst and honeycomb noble metal catalyst provided in the examples of the present application, the NO conversions of the catalysts for both fresh and aged samples are significantly higher than those of the catalyst samples from comparative samples, and the temperature at which the maximum NO conversion of the fresh catalyst sample occurs is lower than those of the catalyst samples from comparative samples. The diffusion of noble metal at the grain boundary and surface enables to form a multiphase interface, which can reduce the activation energy of lattice oxygen and increase the quantity of active oxygen, while avoiding the migration, agglomeration, and growth of the noble metal at high temperatures. Therefore, the grain boundary and surface-loaded noble metal catalyst and the honeycomb noble metal catalyst provided in the examples of the present application can significantly improve the low-temperature catalytic activity and high-temperature stability for NO oxidation.
In conclusion, The present application relates to a grain boundary and surface-loaded noble metal catalyst and a preparation method and an application thereof, wherein the noble metal G is dispersed at the grain boundary and surface of alumina and/or a rare earth manganese-zirconium composite oxide to form a multiphase interface, which achieves the following beneficial technical effects: firstly, the multiphase interface has a larger steric hindrance and a stronger anchoring effect, which can inhibit the migration, agglomeration, and growth of the noble metal at high temperatures, increase the high-temperature stability of the noble metal, and reduce the usage of the noble metal; secondly, the multiphase interface exhibits a synergistic catalytic effect, which can reduce the activation energy of lattice oxygen and increase the quantity of active oxygen, thereby enhancing the NO oxidation and low-temperature catalytic activity.
It will be understood that the specific embodiments described herein are only used to explain the application, and are not intended to limit the application. Therefore, any modification, equivalent substitution, improvement, etc. made without departing from the spirit and principle of the application should be included within the scope of the claims of the application. In addition, the appended claims of the present application are intended to cover the full range of variations and modifications that fall within the scope and boundaries of the appended claims, or equivalent forms of such scope and boundaries.
Number | Date | Country | Kind |
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202210135505.3 | Feb 2022 | CN | national |
This application is a continuation of International Application No. PCT/CN2023/075761, filed on Feb. 13, 2023, which claims priority to Chinese Patent Application No. 202210135505.3, filed on Feb. 14, 2022. All of the aforementioned applications are incorporated herein by reference in their entireties.
Number | Date | Country | |
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Parent | PCT/CN2023/075761 | Feb 2023 | WO |
Child | 18770265 | US |