Patent Application
20240181391
The present invention relates to an exhaust gas purifying catalyst composition and an exhaust gas purifying catalyst.
Exhaust gas emitted from an internal-combustion engine of an automobile, a motorcycle or the like contains harmful components, such as hydrocarbons (THC), carbon monoxide (CO) and nitrogen oxide (NOx). As an exhaust gas purifying catalyst that purifies and detoxifies these harmful components, a three-way catalyst having a catalytic activity to oxidize THC and convert it to water and carbon dioxide, to oxidize CO and convert it to carbon dioxide as well as to reduce NOx and convert it to nitrogen, has been used.
In an exhaust gas purifying catalyst such as a three-way catalyst, an Al-based oxide such as alumina (Al2O3), a Ce—Zr-based composite oxide, and the like are used as a carrier that supports a catalytically active component (e.g., a particle of a noble metal such as Pt, Pd, or Rh) (for example, Patent Documents 1 and 2). In the present specification, “Al-based oxide” means an oxide containing Al, wherein the amount of Al in terms of Al2O3 is 70% by mass or more based on the mass of the oxide, and “Ce—Zr-based composite oxide” means a composite oxide containing Ce and Zr, wherein the amount of Ce in terms of CeO2 is 5% by mass or more and 90% by mass or less based on the mass of the composite oxide.
A Ce—Zr-based composite oxide is a material (OSC material) that has an oxygen storage capacity (OSC), which mitigates fluctuations in the oxygen concentration in the exhaust gas and expands the operating window of the catalyst. A Ce-based oxide such as cerium oxide (CeO2) is also used as an OSC material (for example, Patent Document 2). However, since CeO2 has a low oxygen storage capacity, CeO2 is generally not used as a carrier for supporting a catalytically active component of a three-way catalyst. In the present specification, “Ce-based oxide” means an oxide containing Ce, wherein the amount of Ce in terms of CeO2 is 80% by mass or more based on the mass of the oxide.
A Ce-based oxide has high affinity to a catalytically active component (for example, a particle of a noble metal such as Pt, Pd, or Rh), but has low heat resistance. On the other hand, a Ce—Zr-based composite oxide has high heat resistance, but has relatively low affinity to a catalytically active component (for example, a particle of a noble metal such as Pt, Pd, or Rh). Therefore, by using a Ce-based oxide and a Ce—Zr-based composite oxide together as a carrier for supporting a catalytically active component, the weak point of one can be compensated for by the other. However, even if a Ce-based oxide and a Ce—Zr-based composite oxide are used in combination, the exhaust gas purification performance may decrease.
For example, when CeO2 is used as a carrier for supporting a catalytically active component, the low heat resistance of CeO2 leads to CeO2 aggregation, disappearance of small pores of CeO2 (that is, decrease in specific surface area), and the like. As a result, the catalytically active component is burled, and the exhaust gas purification performance may decrease. The CeO2 aggregation and the decrease in specific surface area of CeO2 tend to occur in a high-temperature environment, so the decrease in exhaust gas purification performance tends to occur after exposure to a high-temperature environment. In the present specification, “high temperature” means a temperature of, for example, 800° C. or higher, and particularly 900° C. or higher.
Therefore, it is an object of the present invention to provide an exhaust gas purifying catalyst composition and an exhaust gas purifying catalyst, each of which utilizes a Ce-based oxide and a Ce—Zr-based composite oxide, and has improved exhaust gas purification performance (particularly improved exhaust gas purification performance after exposure to a high-temperature environment.
The present inventors have found that, in an exhaust gas purifying catalyst composition and an exhaust gas purifying catalyst, each of which utilizes a Ce-based oxide and a Ce—Zr-based composite oxide, the exhaust gas purification performance (in particular, the exhaust gas purification performance after exposure to a high-temperature environment) is improved by adjusting the crystallite size of CeO2 in the Ce-based oxide.
The present invention has been completed based on the findings described above, and includes the following inventions.
[1] An exhaust gas purifying catalyst composition containing a Ce-based oxide particle, a Ce—Zr-based composite oxide particle, and a noble metal element,
The present invention provides an exhaust gas purifying catalyst composition and an exhaust gas purifying catalyst, each of which utilizes a Ce-based oxide and a Ce—Zr-based composite oxide, and has improved exhaust gas purification performance (particularly improved exhaust gas purification performance after exposure to a high-temperature environment.
The exhaust gas purifying catalyst composition of the present invention will now be described.
The exhaust gas purifying catalyst composition of the present invention contains a Ce-based oxide particle. In the present specification, unless otherwise specified, “Ce-based oxide particle” means a Ce-based oxide particle contained in the exhaust gas purifying catalyst composition of the present invention, which is distinguished from a Ce-based oxide particle used as a raw material for the exhaust purifying catalyst composition of the present invention (hereinafter referred to as “Ce-based oxide particle as a raw material”).
The Ce-based oxide particle is composed of a Ce-based oxide. The amount of Ce in terms of CeO2 in the Ce-based oxide particle is preferably 80% by mass or more, more preferably 85% by mass or more, further preferably 90% by mass or more, further preferably 95% by mass or more, and further preferably 99% by mass or more, based on the mass of the Ce-based oxide particle. This improves the affinity of the Ce-based oxide particle to a catalytically active component, and suppresses the occurrence of sintering between a catalytically active component and another catalytically active component, each of which is supported on the Ce-based oxide particle. Therefore, the degree of dispersion of the catalytically active component is improved, and the exhaust gas purification performance of the exhaust gas purifying catalyst composition is improved. Such effects are pronounced in an exhaust gas purifying catalyst composition after it has been exposed to a high-temperature environment. This is because sintering between a catalytically active component and another catalytically active component, each of which is supported on the Ce-based oxide particle, tends to occur after exposure to a high-temperature environment. The upper limit is theoretically 100% by mass, but in reality, can be less than 100% by mass, considering the presence of unavoidable impurities.
The amount of Ce in terms of CeO2 in the Ce-based oxide particle can be measured by analyzing a sample obtained from the exhaust gas purifying catalyst composition of the present invention by energy dispersive X-ray spectroscopy (EDS (also referred to as EDX)) to obtain an element mapping, and performing EDS elemental analysis on a designated particle in the obtained element mapping. Specifically, the amount of a specified element in terms of oxide in the designated particle can be measured by qualitatively identifying (color-coding) a Ce-based oxide particle, a Ce—Zr-based composite oxide particle and the other particle(s) (e.g., an Al-based oxide particle) by elemental mapping and performing composition analysis (elemental analysis) on the designated particle.
From the viewpoint of further improving the affinity of the Ce-based oxide particle to a catalytically active component and more effectively suppressing the occurrence of sintering between a catalytically active component and another catalytically active component, each of which is supported on the Ce-based oxide particle, the amount of Zr in terms of ZrO2 in the Ce-based oxide particle is preferably less than 10% by mass, more preferably 5% by mass or less, further preferably 3% by mass or less, and further preferably 1% by mass or less, based on the mass of the Ce-based oxide particle. The lower limit is zero. The amount of Zr in terms of ZrO2 in the Ce-based oxide particle is smaller than the amount of Zr in terms of ZrO2 in a Ce—Zr-based composite oxide particle, and in this respect, the Ce-based oxide particle is distinguished from a Ce—Zr-based composite oxide particle. The method for measuring the amount of Zr in terms of ZrO2 in the Ce-based oxide particle is the same as the method for measuring the amount of Ce in terms of CeO2 in the Ce-based oxide particle.
The crystallite size of CeO2 in the Ce-based oxide particle is preferably 10 nm or more, more preferably 20 nm or more, and further preferably 30 nm or more. This suppresses Ce-based oxide particle aggregation, disappearance of small pores of the Ce-based oxide particle (that Is, decrease in specific surface area), and burial of a catalytically active component in the Ce-based oxide particle caused by the aggregation and the disappearance. Therefore, the degree of dispersion of the catalytically active component is improved, and the exhaust gas purification performance of the exhaust gas purifying catalyst composition is improved. Such effects are pronounced in an exhaust gas purifying catalyst composition after it has been exposed to a high-temperature environment. This is because the Ce-based oxide particle aggregation, the decrease in specific surface area of the Ce-based oxide particle, and the burial of the catalytically active component in the Ce-based oxide particle caused by the aggregation and the decrease tend to occur after exposure to a high-temperature environment. The upper limit of the crystallite size of CeO2 in the Ce-based oxide particle is, for example, 200 nm, preferably 100 nm, and more preferably 55 nm. Each of these upper limits may be combined with any of the above-described lower limits.
The method for measuring the crystallite size of CeO2 in the Ce-based oxide particle is as follows. X-ray diffraction (XRD) is performed using a powder sample obtained from the exhaust gas purifying catalyst composition of the present invention and a commercially available X-ray diffractometer. In the obtained XRD pattern, among the peaks derived from CeO2, the peak present at 2θ=55 to 58° and the peak present at 2θ=46 to 49° are identified, and the Scherrer equation is applied to the identified peaks to measure the crystallite size. The specific measuring method is as described in the Examples. The crystallite size determined from the peak present at 2θ=55 to 58° and the crystallite size determined from the peak present at 2θ=46 to 49° are compared, and the larger crystallite size is selected as the crystallite size of CeO2 in the Ce-based oxide particle. When, in the obtained XRD pattern, it is impossible to identify one of the peak present at 2θ=55 to 58° and the peak present at 2θ=46 to 49° among the peaks derived from CeO2 due to a peak(s) derived from a component(s) other than CeO2, the crystallite size obtained from the peak that can be identified is taken as the crystallite size of CeO2 in the Ce-based oxide particle.
The crystallite size of CeO2 in the Ce-based oxide particle may be adjusted, for example, by adjusting firing conditions when producing the Ce-based oxide particle, or may be adjusted by providing a crystallization step (e.g., exposing to a hydrothermal condition) in the production stage of the Ce-based oxide particle.
From the viewpoint of more effectively exerting the above-described effects of the Ce-based oxide particle, the amount of the Ce-based oxide particle in the exhaust gas purifying catalyst composition of the present invention is preferably 1.0% by mass or more, more preferably 2.0% by mass or more, further preferably 3.0% by mass or more, further preferably 5.0% by mass or more, and further preferably 10% by mass or more, based on the mass of the exhaust gas purifying catalyst composition of the present invention. In addition, from the viewpoint of further improving the specific surface area of the exhaust gas purifying catalyst composition (in particular, the specific surface area after exposure to a high-temperature environment) by relatively increasing the amount of a component(s) other than the Ce-based oxide particle (e.g., the amount of a Ce—Zr-based composite oxide particle, the amount of the other particle(s), etc.), the amount of the Ce-based oxide particle in the exhaust gas purifying catalyst composition of the present invention is preferably 50% by mass or less, more preferably 30% by mass or less, further preferably 25% by mass or less, further preferably 20% by mass or less, and further preferably 15% by mass or less, based on the mass of the exhaust gas purifying catalyst composition of the present invention. Each of these upper limits may be combined with any of the above-described lower limits.
The method for measuring the amount of the Ce-based oxide particle in the exhaust gas purifying catalyst composition of the present invention is performed according to the following procedures (A) to (D).
(A) Elemental analysis using inductively coupled plasma atomic emission spectroscopy (ICP), X-ray fluorescence spectroscopy (XRF), scanning electron microscopy-energy dispersive X-Ray spectroscopy (SEM-EDX) or the like is performed on a sample obtained from the exhaust gas purifying catalyst composition to identify the types of constituent elements of the entire sample, and to obtain the content of each Identified element in terms of oxide.
(B) Elemental mapping by SEM observation and SEM-EDX is performed on a sample obtained from the exhaust gas purifying catalyst composition, and the types of particles contained in the sample (including a Ce-based oxide particle, a Ce—Zr-based composite oxide particle, and the other particle(s) (e.g., an Al-based oxide particle)) are identified.
(C) For each type of particle, elemental analysis by SEM-EDX is performed on a plurality of randomly selected particles (for example, 50 particles) to identify the types of constituent elements of the particles and to obtain the content of each identified element in terms of oxide. For each type of particle, the average value of the content of each element is taken as the content of each element.
(D) The content of each type of particle in the sample is calculated by drawing up and solving equations representing the relationship among the content of each element in the sample, the content of each element in each type of particle, and the content of each type of particle in the sample.
For example, when the Ce source, the Zr source, and the Al source in the exhaust gas purifying catalyst composition of the present invention consist of the three types, that is, a Ce-based oxide particle, a Ce—Zr-based composite oxide particle, and an Al-based oxide particle, the amount of the Ce-based oxide particle is determined as follows.
First, on a sample obtained from the exhaust gas purifying catalyst composition of the present invention, SEM-EDX analysis is performed on five randomly selected fields of view (each field of view containing 20 or more particles) to identify the types of constituent elements of the entire sample and to obtain the content (average value) of each identified element in terms of oxide.
Next, elemental mapping by SEM observation and SEM-EDX is performed on a sample obtained from the exhaust gas purifying catalyst composition, and the types of particles contained in the sample (including the Ce-based oxide particle, the Ce—Zr-based composite oxide particle, and the Al-based oxide particle) are identified.
Next, for each type of particle, elemental analysis by SEM-EDX is performed on fifty randomly selected particles to identify the types of constituent elements of the particles and to obtain the content (average value) of each identified element in terms of oxide.
Through the above procedure, the following contents are obtained.
Next, the content of each type of particle in the sample is calculated by drawing up and solving equations representing the relationship among the content of each element in the sample, the content of each element in each type of particle, and the content of each type of particle in the sample.
Specifically, assuming that the content (on a mass basis) of the Ce-based oxide particle, the content (on a mass basis) of the Ce—Zr-based composite oxide particle, and the content (on a mass basis) of the other particle in the exhaust gas purifying catalyst composition of the present invention are X, Y and Z, respectively, the following Equations (1) to (3) are true.
P
T
=X×P
1
+Y×P
2
+Z×P
3 (1)
Q
T
=X×Q
1
+Y×Q
2
+Z×Q
3 (2)
R
T
=X×R
1
+Y×R
2
+Z×R
3 (3)
From the above equations (1) to (3), X, Y and Z are obtained, and from X, the amount of the Ce-based oxide particle in the exhaust gas purifying catalyst composition of the present invention is obtained.
If the average particle size of the Ce-based oxide particle is too small, a solid phase reaction will proceed at the interface between the Ce-based oxide particle and a Ce—Zr-based composite oxide particle, and the Ce-based oxide particle will be no longer present as a particle. The solid phase reaction at the interface between the Ce-based oxide particle and a Ce—Zr-based composite oxide particle tends to occur after exposure to a high-temperature environment. On the other hand, if the average particle size of the Ce-based oxide particle is too large, the dispersibility of the Ce-based oxide particle will decrease, and the contact property of the Ce-based oxide particle with a catalytically active component will deteriorate. Therefore, from the viewpoint of more effectively exerting the above effects of the Ce-based oxide particle, the average particle size of the Ce-based oxide particle is preferably 0.10 μm or more and 15 μm or less, more preferably 0.50 μm or more and 12 μm or less, further preferably 1.0 μm or more and 10 μm or less, and further preferably 2.0 μm or more and 7.0 μm or less.
A method of measuring the average particle size of the Ce-based oxide particle is as follows. A sample obtained from the exhaust gas purifying catalyst composition of the present Invention is observed using a scanning electron microscope, and unidirectional particle diameters (Feret diameters) of 100 Ce-based oxide particles arbitrarily selected from the visual field are measured to define an average value as the average particle size of the Ce-based oxide particle. When producing the exhaust gas purifying catalyst composition of the present invention, the average particle size of a Ce-based composite oxide particle as a raw material is maintained, and thus the average particle size of the Ce-based composite oxide particle is usually the same as the average particle size of a Ce-based composite oxide particle as a raw material.
The average particle size of the Ce-based oxide particle may be adjusted, for example, by using a known pulverization method such as a ball mill, or by using a granulation method such as a spray drying method when producing the Ce-based oxide particle.
The Ce-based oxide particle is used as a carrier of a catalytically active component. From the viewpoint of improving the supportability of the catalytically active component, the Ce-based oxide particle is preferably porous. The Ce-based oxide particle is distinguished from ceria used as a binder (hereinafter referred to as “ceria binder”). The ceria binder is derived from a ceria sol used as a material for the catalyst composition or from a water-soluble cerium salt (e.g., cerium nitrate or cerium nitrate) used as a material for the catalyst composition.
The Ce-based oxide particle may contain one or more types of metal elements other than Ce. Examples of such a metal element other than Ce include rare earth elements such as Y, Pr, Sc, La, Nd, Sm, Eu, Gd, Tb, Dy, Ho, Er, Tm, Yb, and Lu, transition metal elements such as Fe, Mn, Ni, and Zr, and the like. Such a metal element other than Ce may form a solid solution phase together with Ce and O, or may form a single phase, which is a crystal phase or an amorphous phase (for example, an oxide phase of a metal element other than Ce), or may form both a solid solution phase and a single phase.
The exhaust gas purifying catalyst composition of the present invention contains a Ce—Zr-based composite oxide particle. In the present specification, unless otherwise specified, “Ce—Zr-based composite oxide particle” means a Ce—Zr-based composite oxide particle contained in the exhaust gas purifying catalyst composition of the present invention, which is distinguished from a Ce—Zr-based composite oxide particle used as a raw material for the exhaust purifying catalyst composition of the present Invention (hereinafter referred to as “Ce—Zr-based composite oxide particle as a raw material”).
The Ce—Zr-based composite oxide particle has an oxygen storage capacity (i.e., an ability to absorb oxygen when the oxygen concentration in exhaust gas is high and release oxygen when the oxygen concentration in exhaust gas is low), and mitigate fluctuations in the oxygen concentration in exhaust gas and expand the operating window of a catalytically active component. Therefore, the exhaust gas purification performance of the exhaust gas purifying catalyst composition is improved.
The Ce—Zr-based composite oxide particle is composed of a Ce—Zr-based composite oxide. From the viewpoint of improving the oxygen storage capacity of the Ce—Zr-based composite oxide particle, the amount of Ce in terms of CeO2 in the Ce—Zr-based composite oxide particle is preferably 5% by mass or more and 90% by mass or less, more preferably 5% by mass or more and 70% by mass or less, further preferably 7% by mass or more and 60% by mass or less, and further preferably 10% by mass or more and 50% by mass or less, based on the mass of the Ce—Zr-based composite oxide particle. The method for measuring the amount of Ce in terms of CeO2 in the Ce—Zr-based composite oxide particle is the same as the method for measuring the amount of Ce in terms of CeO2 in the Ce-based oxide particle.
From the viewpoint of further improving the heat resistance of the Ce—Zr-based composite oxide particle and further improving the exhaust gas purification performance (particularly, the exhaust gas purification performance after being exposed to a high temperature environment) of the exhaust gas purifying catalyst composition, the amount of Zr in terms of ZrO2 in the Ce—Zr-based composite oxide particle is preferably 10% by mass or more and 95% by mass or less, more preferably 20% by mass or more and 95% by mass or less, further preferably 40% by mass or more and 95% by mass or less, and further preferably 50% by mass or more and 90% by mass or less, based on the mass of the Ce—Zr-based composite oxide particle. The method for measuring the amount of Zr in terms of ZrO2 in the Ce—Zr-based composite oxide particle is the same as the method for measuring the amount of Ce in terms of CeO2 in the Ce-based oxide particle.
From the viewpoint of further improving the oxygen storage capacity and heat resistance of the Ce—Zr-based composite oxide particle and further improving the exhaust gas purification performance (particularly, the exhaust gas purification performance after being exposed to a high temperature environment) of the exhaust gas purifying catalyst composition, the total of the amount of Ce in terms of CeO2 and the amount of Zr in terms of ZrO2 in the Ce—Zr-based composite oxide particle is preferably 70% by mass or more, more preferably 75% by mass or more, further preferably 80% by mass or more, and further preferably 85% by mass or more, based on the mass of the Ce—Zr-based composite oxide particle. The upper limit is 100% by mass.
From the viewpoint of more effectively exerting the above-described effects of the Ce—Zr-based composite oxide particle, the amount of the Ce—Zr-based composite oxide particle in the exhaust gas purifying catalyst composition of the present invention is preferably 5% by mass or more, more preferably 15% by mass or more, and further preferably 30% by mass or more, based on the mass of the exhaust gas purifying catalyst composition of the present invention. In addition, from the viewpoint of more effectively exerting the above-described effects of the Ce-based oxide particle by relatively Increasing the amount of the Ce-based oxide particle, the amount of the Ce—Zr-based composite oxide particle in the exhaust gas purifying catalyst composition of the present invention is preferably 98.99% by mass or less, more preferably 80% by mass or less, and further preferably 70% by mass or less, based on the mass of the exhaust gas purifying catalyst composition of the present Invention. Each of these upper limits may be combined with any of the above-described lower limits. The method for measuring the amount of the Ce—Zr-based composite oxide particle in the exhaust gas purifying catalyst composition of the present invention is the same as the method for measuring the amount of the Ce-based oxide particle in the exhaust gas purifying catalyst composition of the present invention.
From the viewpoint of balancing the above-described effects of the Ce-based oxide particle and the above-described effects of the Ce—Zr-based composite oxide particle, and further improving the exhaust gas purification performance of the exhaust gas purifying catalyst composition (in particular, the exhaust gas purification performance after exposure to a high-temperature environment), the mass ratio of the amount of the Ce—Zr-based composite oxide particle to the amount of the Ce-based oxide particle in the exhaust gas purifying catalyst composition of the present invention is preferably 0.5 or more and 70 or less, more preferably 1.0 or more and 25 or less, and further preferably 1.5 or more and 15 or less.
The average particle size of the Ce—Zr-based composite oxide particle is preferably 0.1 μm or more and 15 μm or less, more preferably 0.5 μm or more and 12 μm or less, and further preferably 1 μm or more and 10 μm or less. The method for measuring the average particle size of the Ce—Zr-based composite oxide particle is the same as the method for measuring the average particle size of the Ce-based oxide particle. The average particle size of the Ce—Zr-based composite oxide particle can be adjusted in the same manner as the average particle size of the Ce-based oxide particle. When producing the exhaust gas purifying catalyst composition of the present invention, the average particle size of a Ce—Zr-based composite oxide particle as a raw material is maintained, and thus the average particle size of the Ce—Zr-based composite oxide particle is usually the same as the average particle size of a Ce—Zr-based composite oxide particle as a raw material.
The Ce—Zr-based composite oxide particle is used as a carrier of a catalytically active component. From the viewpoint of improving the supportability of the catalytically active component, the Ce—Zr-based composite oxide particle is preferably porous.
In the Ce—Zr-based composite oxide particle, Ce, Zr, and O preferably form a solid solution phase. In addition to the solid solution phase, Ce, Zr, and O may form a single phase (CeO2 phase and/or ZrO2 phase), which is a crystalline phase or an amorphous phase.
The Ce—Zr-based composite oxide particle may contain one or more types of metal elements other than Ce and Zr. Examples of such a metal element other than Ce and Zr include rare earth elements other than Ce and the like. Examples of such a rare earth element other than Ce include Y, Pr, Sc, La, Nd, Sm, Eu, Gd, Tb, Dy, Ho, Er, Tm, Yb, and Lu. Such a metal element other than Ce and Zr may form a solid solution phase together with Ce, Zr and O, or may form a single phase, which is a crystal phase or an amorphous phase, or may form both a solid solution phase and a single phase.
From the viewpoint of balancing the above-described effects of the Ce-based oxide particle and the above-described effects of the Ce—Zr-based composite oxide particle, and further improving the exhaust gas purification performance of the exhaust gas purifying catalyst composition (in particular, the exhaust gas purification performance after exposure to a high-temperature environment), in an XRD pattern of the exhaust gas purifying catalyst composition of the present invention measured using a CuKα ray, a ratio of an intensity of a peak present at 2θ=55 to 58° among peaks from the Ce-based oxide particle to an intensity of a peak present at 2θ=58 to 61° among peaks from the Ce—Zr-based composite oxide particle is preferably 0.10 or more and 10 or less, more preferably 0.01 or more and 5 or less, and further preferably 0.01 or more and 3 or less. Among the peaks derived from the Ce-based oxide particle, the peak present at 2θ=55 to 58° is the peak derived from CeO2, and among the peaks derived from the Ce—Zr-based composite oxide particle, the peak at 2θ=58 to 61° is the peak derived from Ce—Zr-based composite oxide.
The XRD pattern can be obtained by performing XRD with CuKα using a powder sample obtained from the exhaust gas purifying catalyst composition of the present invention and a commercially available powder X-ray diffractometer. Specific XRD conditions are as mentioned in the Examples.
The exhaust gas purifying catalyst composition of the present invention contains at least one type of noble metal element. Such a noble metal element can be selected, for example, from Au, Ag, Pt, Pd, Rh, Ir, Ru, Os, and the like, and is preferably selected from Rh and Pt.
The noble metal element contained in the exhaust gas purifying catalyst composition of the present invention is in a form capable of functioning as a catalytic active component, for example, in the form of a metal, an alloy containing the noble metal element, a compound containing the noble metal element (for example, an oxide of the noble metal element), or the like.
From the viewpoint of balancing the exhaust gas purification performance and the cost, the amount of the noble metal element in the exhaust gas purifying catalyst composition of the present invention is preferably 0.010% by mass or more and 20% by mass or less, more preferably 0.050% by mass or more and 10% by mass or less, and further preferably 0.10% by mass or more and 5.0% by mass or less, based on the mass of the exhaust gas purifying catalyst composition of the present invention. In the present specification, “amount of the noble metal element” means, when the catalyst composition contains one type of noble metal element, the amount of the one type of noble metal element in terms of metal, and when the catalyst composition contains two or more types of noble metal elements, the total of the amounts of the two or more types of noble metal elements in terms of metal.
The amount of the noble metal element in the exhaust gas purifying catalyst composition of the present invention can be measured by analyzing a sample obtained from the exhaust gas purifying catalyst composition of the present invention by EDS or WDS (wavelength dispersive X-ray fluorescence spectrometer) to obtain an element mapping, and performing EDS elemental analysis on a designated particle in the obtained element mapping.
The noble metal element preferably includes a noble metal element supported on the Ce-based oxide particle and a noble metal element supported on the Ce—Zr-based composite oxide particle. At a low to medium temperature, the noble metal element supported on the Ce-based oxide particle tends to exhibit an exhaust gas purification performance, and at a high temperature, the noble metal element supported on the Ce—Zr-based composite oxide particle tends to exhibit an exhaust gas purification performance. Therefore, by using the noble metal element supported on the Ce-based oxide particle and the noble metal element supported on the Ce—Zr-based composite oxide particle, an excellent exhaust gas purification performance is exhibited over a wide temperature range. In particular, when the exhaust gas purifying catalyst composition of the present invention is in a high-temperature environment, Ce-based oxide particle aggregation, disappearance of small pores of the Ce-based oxide particle (i.e., decrease in specific surface area), and burial of a catalytically active component in the Ce-based oxide particle caused by the aggregation and the disappearance are suppressed. Thus, an excellent exhaust gas purification performance is exhibited at a low to medium temperature after exposure to a high-temperature environment. As used herein, the term “low to medium temperature” means, for example, a temperature of from 50° C. to 400° C., and preferably, from 100° C. to 350° C. The term “supported” refers to a state in which a catalytically active component such as a noble metal is physically or chemically absorbed or retained on the outer surface or on the inner surface of the pores of the Ce-based oxide particle or the Ce—Zr-based composite oxide particle. For example, a sample obtained from the exhaust gas purifying catalyst composition of the present invention is analyzed by SEM-EDX and when a catalytically active component and a Ce-based oxide particle are present in the same region, it can be determined that the catalytically active component is supported on the Ce-based oxide particle, and when a catalytically active component and a Ce—Zr-based composite oxide particle are present in the same region, it can be determined that the catalytically active component is supported on the Ce—Zr-based composite oxide particle. The amount of the noble metal element supported on the Ce-based oxide particle is preferably 0.05% by mass or more, and more preferably 0.10% by mass or more based on the mass of the Ce-based oxide particle. The upper limit is, for example, 20% by mass. The amount of the noble metal element supported on the Ce—Zr-based composite oxide particle is preferably 0.05% by mass or more, and more preferably 0.10% by mass or more based on the mass of the Ce—Zr-based composite oxide particle. The upper limit is, for example, 20% by mass.
The exhaust gas purifying catalyst composition of the present invention may contain one or more types of inorganic oxide particles other than the Ce-based oxide particle and the Ce—Zr-based composite oxide particle (hereinafter referred to as “the other particle(s)”). In the present specification, unless otherwise specified, “the other particle(s)” means the other particle(s) contained in the exhaust gas purifying catalyst composition of the present invention, which is/are distinguished from the other particle(s) used as a raw material for the exhaust purifying catalyst composition of the present invention (hereinafter referred to as “the other particle(s) as a raw material”).
The other particle(s) is/are composed of an oxide containing a metal element(s) other than Ce and Zr. Examples of the other particle(s) include an Al-based oxide particle, a zirconia particle, a silica particle, a titania particle, and the like.
The Al-based oxide particle generally has higher heat resistance than the Ce-based oxide particle and the Ce—Zr-based composite oxide particle. Therefore, the specific surface area of the exhaust gas purifying catalyst composition (in particular, the specific surface area after exposure to a high-temperature environment) is improved, and the exhaust gas purification performance of the exhaust gas purifying catalyst composition (in particular, the exhaust gas purification performance after exposure to a high-temperature environment) is improved.
The Al-based oxide particle is composed of an Al-based oxide. The Al-based oxide particle may or may not contain an element(s) other than Al and O.
Such an element(s) other than Al and O can be selected from B, Si, rare earth elements (e.g., Y, Ce, La, Nd, Pr, Sm, Gd, etc.), Zr, Cr, alkaline earth metal elements (e.g., Mg, Ca, Sr, Ba, etc.), and the like, but it is preferable to select such an element(s) from Ce, La, Sr, Ba, and the like, from the viewpoint of improving the heat resistance of the Al-based oxide particle.
Examples of the Al-based oxide include alumina (an oxide consisting of Al and O), an oxide obtained by modifying the surface of alumina with an element(s) other than Al and O, and an oxide obtained by dissolving an element(s) other than Al and O in alumina. Specific examples of such an Al-based oxide containing an element(s) other than Al and O include alumina-silica, alumina-silicate, alumina-zirconia, alumina-chromia, alumina-ceria, alumina-lanthana, and the like.
In the Al-based oxide particle, an element(s) other than Al and O may form a solid solution phase together with Al and O, or may form a single phase that is a crystal phase or an amorphous phase (for example, an oxide phase of an element other than Al and O), or may form both a solid solution phase and a single phase.
When the Al-based oxide particle contain an element(s) other than Al and O, the amount of Al in terms of Al2O3 in the Al-based oxide particle is preferably 70% by mass or more and 99.9% by mass or less, more preferably 80% by mass or more and 99.5% by mass or less, and further preferably 90% by mass or more and 99% by mass or less, based on the mass of the Al-based oxide particle, from the viewpoint of improving the heat resistance.
From the viewpoint of improving the specific surface area (in particular, the specific surface area after exposure to a high-temperature environment) and securing a sufficient amount of a co-catalyst (e.g., the Ce-based oxide particle, the Ce—Zr-based composite oxide particle, etc.), the amount of the Al-based oxide particle in the exhaust gas purifying catalyst composition of the present invention is preferably 10% by mass or more and 90% by mass or less, more preferably 15% by mass or more and 70% by mass or less, and further preferably 20% by mass or more and 60% by mass or less, based on the mass of the exhaust gas purifying catalyst composition of the present invention. The method for measuring the amount of the Al-based oxide particle in the exhaust gas purifying catalyst composition of the present invention is the same as the method for measuring the amount of the Ce-based oxide particle in the exhaust gas purifying catalyst composition of the present invention.
From the viewpoint of improving the specific surface area (particularly, the specific surface area after exposure to a high-temperature environment) and securing a sufficient amount of the co-catalyst, the mass ratio of the amount of the Al-based oxide particle to the amount of the Ce-based oxide particle in the exhaust gas purifying catalyst composition of the present invention is preferably 0.1 or more and 10 or less, more preferably 0.2 or more and 5 or less, and further preferably 0.3 or more and 3 or less.
From the viewpoint of achieving both the heat resistance of the Al-based oxide particle and the coatability of the Al-based oxide particle to the substrate, the average particle size of the Al-based oxide particle is preferably 1 μm or more and 50 μm or less, more preferably 2 μm or more and 30 μm or less, and further preferably 4 μm or more and 20 μm or less. The method for measuring the average particle size of the Al-based oxide particle is the same as the method for measuring the average particle size of the Ce-based oxide particle. The average particle size of the Al-based oxide particle can be adjusted in the same manner as the average particle size of the Ce-based oxide particle. When producing the exhaust gas purifying catalyst composition of the present invention, the average particle size of an Al-based oxide particle as a raw material is maintained, and thus the average particle size of the Al-based oxide particle is usually the same as the average particle size of an Al-based oxide particle as a raw material.
The other particle(s) is/are used as a carrier of a catalytically active component. From the viewpoint of improving the supportability of the catalytically active component, the other particle(s) is/are preferably porous. The Al-based oxide particle is distinguished from alumina used as a binder (hereinafter referred to as “alumina binder”). The alumina binder is derived from an alumina sol used as a material for the catalyst composition.
When the exhaust gas purifying catalyst composition of the present invention contains the other particle(s), the noble metal element may include a noble metal element supported on the other particle(s). The meaning of “supported” is the same as described above. At a high temperature, the exhaust gas purification performance of the noble metal element supported on the other particle(s) tends to be exhibited. Therefore, by using the noble metal element supported on the Ce-based oxide particle, the noble metal element supported on the Ce—Zr-based composite oxide particle, and the noble metal element supported on the other particle(s), the exhaust gas purification performance is improved over a wide temperature range. The amount of the noble metal element supported on the other particle(s) is preferably 0.05% by mass or more, and more preferably 0.10% by mass or more, based on the mass of the other particle(s). The upper limit is, for example, 20% by mass.
The exhaust gas purifying catalyst composition of the present invention may contain a stabilizer, a binder, and the like. Examples of the binder include an Inorganic oxide binder such as an alumina sol, a zirconia sol, a titania sol, and a silica sol. Examples of the stabilizer include a nitrate, carbonate, oxide, or sulfate of an alkaline earth metal element (e.g., Sr, Ba, etc.).
The exhaust gas purifying catalyst composition of the present invention is in the form of, for example, a powder, a molded body, or a layer.
The exhaust gas purifying catalyst composition of the present invention can be produced, for example, by mixing a noble metal salt-containing solution, a Ce-based oxide particle as a raw material, a Ce—Zr-based composite oxide particle as a raw material, and optionally other components (e.g., the other particle(s) as a raw material, a binder, a stabilizer, etc.), followed by drying and firing. The fired product may be pulverized as necessary. The noble metal salt may be, for example, a nitrate, an ammine complex salt, a chloride or the like. The solvent contained in the noble metal salt-containing solution is, for example, water (such as ion exchanged water). The noble metal salt-containing solution may contain an organic solvent such as alcohol. The drying temperature is, for example, 50° C. or higher and 150° C. or lower. The drying time is, for example, 1 hour or more and 3 hours or less. The firing temperature is, for example, 300° C. or higher and 700° C. or lower. The firing time is, for example, 1 hour or more and 3 hours or less. The firing can be carried out, for example, in an air atmosphere.
From the viewpoint of adjusting the crystallite size of CeO2 in the Ce-based oxide particle to a desired range, it is preferable to apply a heat load on a Ce-based oxide particle as a raw material to adjust the crystallite size of CeO2 in the Ce-based oxide particle as a raw material. The heat load can be applied, for example, by firing at 1000° C. for 1 hour in an air atmosphere. The crystallite size of CeO2 in the Ce-based oxide particle as a raw material is preferably 10 nm or more, more preferably 20 nm or more, and further preferably 30 nm or more. The upper limit of the crystallite size of CeO2 in the Ce-based oxide particle as a raw material is, for example, 200 nm, preferably 100 nm, and more preferably 55 nm. Each of these upper limits may be combined with any of the above-described lower limits. The method for measuring the crystallite size of CeO2 in the Ce-based oxide particle as a raw material is the same as the method for measuring the crystallite size of CeO2 in the Ce-based oxide particle, except that the measurement is performed using the Ce-based oxide particle as a raw material.
The exhaust gas purifying catalyst according to the present invention will now be described.
The exhaust gas purifying catalyst of the present invention includes a substrate and a catalyst layer of the present invention provided on the substrate. The exhaust gas purifying catalyst of the present invention may have a catalyst layer other than the catalyst layer of the present invention at one or more positions selected from a lower side, an upper side, a downstream side, and an upstream side of the catalyst layer of the present invention.
The substrate can be appropriately selected from substrates of conventional exhaust gas purifying catalysts. Examples of the substrate include a wall-flow substrate and a flow-through substrate.
The material constituting the substrate can be appropriately selected from substrate materials of conventional exhaust gas purifying catalysts. Preferably, the material constituting the substrate is a material that allows the substrate to stably maintain its shape even when the substrate is exposed to, for example, 400° C. or higher exhaust gas. Examples of the material of the substrate include: ceramics such as cordierite, silicon carbide (SiC) and aluminum titanate; and alloys such as stainless steel.
The catalyst layer of the present invention is composed of the exhaust gas purifying catalyst composition of the present invention. That is, the catalyst layer of the present invention includes the Ce-based oxide particle, the Ce—Zr-based composite oxide particle, and the noble metal element. The descriptions in the above sections<Ce-based oxide particle>, <Ce-Zr-based composite oxide particle>, <Noble Metal Element>, and <Other Components>also apply to the catalyst layer of the present invention. When the descriptions apply to the catalyst layer of the present invention, “the exhaust gas purifying catalyst composition of the present invention” is read as “the catalyst layer of the present invention”. However, “the XRD pattern of the exhaust gas purifying catalyst composition of the present invention measured using a CuKα ray” means “the XRD pattern of the composition constituting the catalyst layer of the present invention measured using a CuKα ray.” The composition constituting the catalyst layer of the present invention is, for example, in the form of a powder, and can be scraped off from the catalyst layer of the present invention.
From the viewpoint of balancing the exhaust gas purification performance and the cost, the mass (mass after drying and firing) of the catalyst layer of the present invention per unit volume of the substrate is preferably 10 g/L or more and 300 g/L or less, more preferably 30 g/L or more and 200 g/L or less, and further preferably 50 g/L or more and 150 g/L or less. Here, the volume of the substrate means the apparent volume of the substrate. For example, when the substrate is cylindrical with an outer diameter of 2r, the volume of the substrate is represented by the formula: volume of substrate=Π×r2×(length of the substrate).
Below, an exhaust gas purifying catalyst 1A according to a first embodiment of the present invention will be described with reference to
As depicted in
Together with the exhaust gas purifying catalyst 1A, another exhaust gas purifying catalyst may be disposed in the exhaust gas path in the exhaust pipe P. For example, it is possible that the exhaust gas purifying catalyst 1A is disposed upstream in the exhaust gas path in the exhaust pipe P, and that another exhaust gas purifying catalyst is disposed downstream in the exhaust gas path in the exhaust pipe P. Examples of another exhaust gas purifying catalyst include an exhaust gas purifying catalyst 1B described below and the like.
As depicted in
The above descriptions related to the substrate also apply to the substrate 10.
The catalyst layer 20 is composed of the exhaust gas purifying catalyst composition of the present invention. That is, the catalyst layer 20 includes the Ce-based oxide particle, the Ce—Zr-based composite oxide particle, and the noble metal element. The above descriptions related to the catalyst layer of the present invention also apply to the catalyst layer 20.
As depicted in
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Accordingly, the density of the cells per square inch of the substrate 10 is, for example, 300 cells or more and 900 cells or less. The density of the cells per square inch of the substrate 10 is the total number of the cells 13 per square inch of the cross-section obtained by cutting the substrate 10 along the plane perpendicular to the exhaust gas flow direction X.
As depicted in
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The exhaust gas purifying catalyst 1A can be produced by forming the catalyst layer 20 on the partition wall portion 12 of the substrate 10. For example, the catalyst layer 20 can be formed on the partition wall portion 12 of the substrate 10 by mixing a noble metal salt-containing solution, a Ce-based oxide particle as a raw material, a Ce—Zr-based composite oxide particle as a raw material, and optionally other components (e.g., the other particle(s) as a raw material, a binder, a stabilizer, etc.) to prepare a slurry, coating the slurry on the partition wall portion 12 of the substrate 10, drying, and then firing. The noble metal salt, the solvent contained in the noble metal salt-containing solution, the drying conditions, the firing conditions, the crystallite size of CeO2 in the Ce-based oxide particle as a raw material, and the like are the same as in the method for producing the exhaust gas purifying catalyst composition of the present Invention.
Below, an exhaust gas purifying catalyst 1B according to a second embodiment of the present invention will be described with reference to
As depicted in
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As depicted in
At least one of the catalyst layers 20a and 20b is the catalyst layer of the present Invention, which includes the Ce-based oxide particle, the Ce—Zr-based composite oxide particle, and the noble metal element. The above descriptions related to the catalyst layer of the present invention also apply to the at least one of the catalyst layers 20a and 20b. The composition and the like of the catalyst layer 20a may be the same as or different from those of the catalyst layer 20b.
In the exhaust gas purifying catalyst 1B, exhaust gas that has flowed in through the exhaust gas in-flow side end (opening) of the in-flow cell 13a passes through the porous partition wall 12, and flows out through the exhaust gas out-flow side end (opening) of the out-flow cell 13b. Such a manner is called a wall-flow type.
When exhaust gas that has flowed in through the exhaust gas in-flow side end (opening) of the in-flow cell 13a passes through the porous partition wall 12 in the exhaust gas purifying catalyst 1B, a particulate matter (PM) In the exhaust gas is collected in the pores of the partition wall 12. Accordingly, the exhaust gas purifying catalyst 1B is useful as a gasoline particulate filter for a gasoline engine or a diesel particulate filter for a diesel engine.
The exhaust gas purifying catalyst 1B can be produced by the following method. The end of the substrate 10 on the exhaust gas inflow side is dipped in a slurry for forming the catalyst layer 20a, and the slurry is sucked from the opposite side and dried to form a precursor layer of the catalyst layer 20a. The end of the substrate 10 on the exhaust gas outflow side is dipped in a slurry for forming the catalyst layer 20b, and the slurry is sucked from the opposite side and dried to form a precursor layer of the catalyst layer 20b. After the precursor layer of the catalyst layer 20a and the precursor layer of the catalyst layer 20b are formed, the precursor layers are fired to form the catalyst layer 20a and the catalyst layer 20b, thereby producing the exhaust gas purifying catalyst 1B. The production conditions and the like of the exhaust gas purifying catalyst 1B are the same as those of the exhaust gas purifying catalyst 1A.
The present invention will now be described in more detail below with reference to Examples and Comparative Examples.
A Ce-based oxide powder was prepared as a raw material. The amount of Ce in terms of CeO2 in the Ce-based oxide powder was approximately 100% by mass (>99% by mass). A heat load was applied on the Ce-based oxide powder, and then the average particle size of the Ce-based oxide powder and the crystallite size of CeO2 in the Ce-based oxide powder were measured. The heat load was applied by firing at 1000° C. for 1 hour in an air atmosphere.
A method of measuring the average particle size of the Ce-based oxide powder is as follows. The Ce-based oxide powder was observed using a scanning electron microscope (Miniscope TM3000, manufactured by Hitachi High-Tech Corporation), and unidirectional particle diameters (Feret diameters) of 100 Ce-based oxide particles arbitrarily selected from the visual field were measured to define an average value as the average particle size of the Ce-based oxide powder. The average particle size of the Ce-based oxide powder was 5.0 μm.
The method for measuring the crystallite size of CeO2 in the Ce-based oxide powder is as follows. Using the Ce-based oxide powder and a commercially available powder X-ray diffractometer (“MiniFlex 600”, manufactured by Rigaku Corporation), X-ray diffraction (XRD) was performed under conditions of: X-ray source: CuKα, operating axis: 2θ/θ, measuring method: continuous, counting unit: cps, start angle: 5°, end angle: 90°, sampling width: 0.02°, scan speed: 10°/min, voltage: 40 kV, and current: 150 mA. In the obtained XRD pattern, among the diffraction peaks derived from CeO2, the peak present at 2θ=55 to 58° and the peak present at 2θ=46 to 49° were identified, and using analysis software (“PDXL version 2”, manufactured by Rigaku Corporation), the Scherrer equation was applied to the Identified peaks to automatically calculate the crystallite size. The crystallite size determined from the peak present at 2θ=55 to 58° and the crystallite size determined from the peak present at 2θ=46 to 49° were compared, and the larger crystallite size was selected as the crystallite size of CeO2 in the Ce-based oxide powder. The crystallite size of CeO2 in the Ce-based oxide powder was 40 nm.
In order to produce 100 parts by mass of a catalyst composition, 65.5 parts by mass of a Ce—Zr-based composite oxide powder (the amount of Ce in terms of CeO2: 45% by mass, the amount of Zr in terms of ZrO2: 45% by mass, the amount of La in terms of La2O3: 5% by mass, the amount of Nd in terms of Nd2O3: 5% by mass), 32.5 parts by mass of an Al-based oxide powder (the amount of Al in terms of Al2O3: 99% by mass, the amount of La in terms of La2O3: 1% by mass), and 1.0 parts by mass of a Ce-based oxide powder (the amount of Ce in terms of CeO2: approximately 100% by mass (>99% by mass), the average particle size: 5.0 μm, the crystallite size: 40 nm) were charged into an aqueous solution of diamminedinitritoplatinum in nitric acid (the amount of Pt in terms of metal: 1.0 parts by mass). The mixture was left to stand for 1 hour to impregnate and support the aqueous solution of diamminedinitritoplatinum in nitric acid on the Ce—Zr-based composite oxide powder, the Al-based oxide powder, and the Ce-based oxide powder, and then evaporated and dried to obtain a dry powder. The obtained dry powder was fired at 500° C. for 1 hour in an air atmosphere to obtain a powdery catalyst composition.
Using the catalyst composition obtained in (2) above, XRD was performed in the same manner as described above, and in the obtained XRD pattern, among the peaks derived from CeO2, the peak present at 2θ=55 to 58° and the peak present at 2θ=46 to 49° were identified, and the crystallite size was automatically calculated in the same manner as described above. The crystallite size determined from the peak present at 2θ=55 to 58° and the crystallite size determined from the peak present at 2θ=46 to 49° were compared, and the larger crystallite size was selected as the crystallite size of CeO2 in the catalyst composition. The results are shown in Table 1.
In the XRD pattern obtained in (3) above, the peak present at 20=55 to 58° of the peaks derived from CeO2 and the peak present at 20=58 to 61° of the peaks derived from the Ce—Zr-based composite oxide are adjacent but shown as separate peaks. The height (x) of the peak present at 2θ=55 to 58° of the peaks derived from CeO2 and the height (y) of the peak present at 2θ=58 to 61° of the peaks derived from the Ce—Zr-based composite oxide was obtained, and the peak intensity ratio x/y was calculated. The results are shown in Table 1.
Using a quartz tubular furnace, the catalyst composition obtained in (2) above was heat-treated at 1000° C. for 30 hours in an atmosphere in which 0.5% by volume of 02 gas, 10% by volume of H2O as water vapor, and N2 as the balance were flowing. Using the heat-treated catalyst composition and a metal dispersion measurement device (BELMETAL3 manufactured by MicrotracBel Corp.), the amount of CO adsorbed to the noble metal was measured by a CO pulse method, and the degree of noble metal dispersion was calculated. Here, the degree of noble metal dispersion is the ratio of the number B of noble metal atoms exposed to the noble metal particle surface to the total number A of noble metal atoms in the catalyst composition (Pt in Examples 1 to 4 and Comparative Examples 1 and 2, Rh in Example 5 and Comparative Examples 3 and 4), and is calculated based on the formula: the degree of noble metal dispersion (%)=(B/A)×100. The number B of noble metal atoms exposed to the noble metal particle surface is calculated from the amount of CO adsorbed measured by the CO pulse method, based on the premise that the noble metal atoms exposed to the noble metal particle surface and the CO are adsorbed at a ratio of 1:1. The results are shown in Table 1.
Using a quartz tubular furnace, the catalyst composition obtained in (2) above was heat-treated at 1000° C. for 30 hours in an atmosphere in which 0.5% by volume of 02 gas, 10% by volume of H2O as water vapor, and N2 as the balance were flowing. The heat-treated catalyst composition was filled in a reaction tube, and the exhaust gas purification performance of the catalyst composition after the heat treatment was measured using a fixed bed flow reactor. Specifically, 0.1 g of the heat-treated catalyst composition was filled in the reaction tube, simulated exhaust gas (CO: 3000 ppm, C3H6: 1000 ppm C, NO: 500 ppm, O2: 0.28%, CO2: 14%, H2O: 10%, N2: balance) was introduced into the reaction tube under the conditions of a temperature increase rate of 10° C./min, an air-fuel ratio (A/F) of 14.6, and a total flow rate of 1000 mL/min. It is noted that “A/F” is an abbreviation for Air/Fuel, and is a numerical value indicating the ratio of air to fuel. After the temperature was increased to 600° C. at a rate of temperature increase of 10° C./min, the temperature was maintained for 10 minutes to perform a pretreatment. Then, after cooling, the temperature was increased from 100° C. to 600° C. at a rate of temperature increase of 10° C./min, the amount of NO contained in the simulated exhaust gas flowing out from the outlet of the reaction tube was measured by Fourier transform infrared spectroscopy (FT-IR), and the purification rate was determined based on the following formula. In the following formula, X represents the detected amount when the catalyst composition was not set, and Y represents the detected amount when the catalyst composition was set.
Purification rate (%)=(X−Y)/X×100
The gas temperature in the inlet of the reaction tube when the NO purification efficacy reached 30% was determined as the light-off temperature T30 (° C.). The light-off temperature T30 was determined in the case of temperature rise. The results are shown in Table 1.
The same operations as in Example 1 were performed, except that the added amounts of the Ce—Zr-based composite oxide powder, the Al-based oxide powder, and the Ce-based oxide powder were changed to 64.5 parts by mass, 31.5 parts by mass, and 3.0 parts by mass, respectively. The results are shown in Table 1.
The same operations as in Example 1 were performed, except that the added amounts of the Ce—Zr-based composite oxide powder, the Al-based oxide powder, and the Ce-based oxide powder were changed to 63.5 parts by mass, 30.5 parts by mass, and 5.0 parts by mass, respectively. The results are shown in Table 1.
The same operations as in Example 1 were performed, except that the added amounts of the Ce—Zr-based composite oxide powder, the Al-based oxide powder, and the Ce-based oxide powder were changed to 61.0 parts by mass, 28.0 parts by mass, and 10.0 parts by mass, respectively. The results are shown in Table 1.
The same operations as in Example 1 were performed, except that the added amounts of the Ce—Zr-based composite oxide powder, the Al-based oxide powder, and the Ce-based oxide powder were changed to 66.0 parts by mass, 33.0 parts by mass, and 0.0 parts by mass, respectively. The results are shown in Table 1.
The same operations as in Example 4 were performed, except that a Ce-based oxide powder having a crystallite size of 7 nm was used as the raw material of the catalyst composition instead of the Ce-based oxide powder having a crystallite size of 40 nm. The results are shown in Table 1.
In order to produce 100 parts by mass of a catalyst composition, the same operations as Example 1 were performed, except that 44.6 parts by mass of a Ce—Zr-based composite oxide powder (the amount of Ce in terms of CeO2: 20% by mass, the amount of Zr in terms of ZrO2: 70% by mass, the amount of Nd in terms of Nd2O3: 10% by mass), 36.1 parts by mass of an Al-based oxide powder (the amount of Al in terms of Al2O3: 99% by mass, the amount of La in terms of La2O3: 1% by mass), and 17.8 parts by mass of a Ce-based oxide powder (the amount of Ce in terms of CeO2: approximately 100% by mass (>99% by mass), the average particle size: 5.0 μm, the crystallite size: 40 nm) were charged into an aqueous solution of rhodium nitrate (the amount of Rh in terms of metal: 1.50 parts by mass). The mixture was left to stand for 1 hour to impregnate and support the aqueous solution of rhodium nitrate on the Ce—Zr-based composite oxide powder, the Al-based oxide powder, and the Ce-based oxide powder, and then evaporated and dried to obtain a dry powder. The results are shown in Table 1. Further, the X-ray diffraction pattern obtained in Example 5 is shown in
The same operations as in Example 5 were performed, except that the added amounts of the Ce—Zr-based composite oxide powder, the Al-based oxide powder, and the Ce-based oxide powder were changed to 53.5 parts by mass, 45.0 parts by mass, and 0.0 parts by mass, respectively. The results are shown in Table 1. Further, the X-ray diffraction pattern obtained in Comparative Example 3 is shown in
The same operations as in Example 5 were performed, except that a Ce-based oxide powder having a crystallite size of 7 nm was used as the raw material of the catalyst composition instead of the Ce-based oxide powder having a crystallite size of 40 nm. The results are shown in Table 1. Further, the X-ray diffraction pattern obtained in Comparative Example 4 is shown in
| Number | Date | Country | Kind |
|---|---|---|---|
| 2021-058531 | Mar 2021 | JP | national |
| 2021-058558 | Mar 2021 | JP | national |
| 2021-188894 | Nov 2021 | JP | national |
| Filing Document | Filing Date | Country | Kind |
|---|---|---|---|
| PCT/JP2022/008672 | 3/1/2022 | WO |
