WO2019194187A1 - Material for exhaust gas purification catalyst, catalyst composition for exhaust gas purification, and exhaust gas purification catalyst - Google Patents

Material for exhaust gas purification catalyst, catalyst composition for exhaust gas purification, and exhaust gas purification catalyst Download PDF

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WO2019194187A1
WO2019194187A1 PCT/JP2019/014655 JP2019014655W WO2019194187A1 WO 2019194187 A1 WO2019194187 A1 WO 2019194187A1 JP 2019014655 W JP2019014655 W JP 2019014655W WO 2019194187 A1 WO2019194187 A1 WO 2019194187A1
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exhaust gas
gas purification
composite oxide
formula
purification catalyst
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PCT/JP2019/014655
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French (fr)
Japanese (ja)
Inventor
亮 竹内
慶徳 遠藤
大典 岩倉
庸裕 田中
三郎 細川
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三井金属鉱業株式会社
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Publication of WO2019194187A1 publication Critical patent/WO2019194187A1/en

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    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D53/00Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
    • B01D53/34Chemical or biological purification of waste gases
    • B01D53/92Chemical or biological purification of waste gases of engine exhaust gases
    • B01D53/94Chemical or biological purification of waste gases of engine exhaust gases by catalytic processes
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J23/00Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00
    • B01J23/16Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of arsenic, antimony, bismuth, vanadium, niobium, tantalum, polonium, chromium, molybdenum, tungsten, manganese, technetium or rhenium
    • B01J23/32Manganese, technetium or rhenium
    • B01J23/34Manganese
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J23/00Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00
    • B01J23/38Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of noble metals
    • B01J23/54Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of noble metals combined with metals, oxides or hydroxides provided for in groups B01J23/02 - B01J23/36
    • B01J23/56Platinum group metals
    • B01J23/64Platinum group metals with arsenic, antimony, bismuth, vanadium, niobium, tantalum, polonium, chromium, molybdenum, tungsten, manganese, technetium or rhenium
    • B01J23/656Manganese, technetium or rhenium
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J37/00Processes, in general, for preparing catalysts; Processes, in general, for activation of catalysts
    • B01J37/02Impregnation, coating or precipitation
    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F01MACHINES OR ENGINES IN GENERAL; ENGINE PLANTS IN GENERAL; STEAM ENGINES
    • F01NGAS-FLOW SILENCERS OR EXHAUST APPARATUS FOR MACHINES OR ENGINES IN GENERAL; GAS-FLOW SILENCERS OR EXHAUST APPARATUS FOR INTERNAL COMBUSTION ENGINES
    • F01N3/00Exhaust or silencing apparatus having means for purifying, rendering innocuous, or otherwise treating exhaust
    • F01N3/08Exhaust or silencing apparatus having means for purifying, rendering innocuous, or otherwise treating exhaust for rendering innocuous
    • F01N3/10Exhaust or silencing apparatus having means for purifying, rendering innocuous, or otherwise treating exhaust for rendering innocuous by thermal or catalytic conversion of noxious components of exhaust

Definitions

  • the present invention relates to an exhaust gas purification catalyst material comprising a complex oxide containing rare earth elements and manganese, an exhaust gas purification catalyst composition containing the complex oxide, and an exhaust gas purification catalyst comprising the exhaust gas purification catalyst composition.
  • Hydrocarbon (HC), carbon monoxide (CO), and nitrogen oxide (NO x ) are contained in exhaust gas emitted from internal combustion engines such as automobiles and motorcycles (also referred to as saddle-type vehicles) such as gasoline engines and diesel engines. Contains harmful ingredients such as.
  • a three-way catalyst has been used for the purpose of purifying and detoxifying these harmful components.
  • a noble metal that causes high costs such as platinum (Pt), palladium (Pd), rhodium (Rh), and alumina, ceria, zirconia, or a composite oxide thereof is arbitrarily combined. Things are used.
  • Patent Document 1 an exhaust purification catalyst in which YbFe x Mn 1-x O 3 is used as a carrier and a catalytically active component is carried on this carrier has been reported.
  • Patent Document 2 an exhaust purification catalyst in which YMnO 3 is used as a carrier and a catalytically active component is supported thereon has been reported.
  • Patent Document 2 an exhaust purification catalyst in which YMnO 3 is used as a carrier has a high exhaust gas purification effect in a low temperature range.
  • the catalyst composition in which the catalytically active component is supported on YbFe x Mn 1-x O 3 described in Patent Document 1 has room for improvement in terms of HC, NO x , and CO purification performance after high-temperature durability. there were. Further, this catalyst composition has room for improvement in terms of thermal stability of OSC (oxygen storage capacity). Further, the catalyst composition described in Patent Document 2 also has insufficient HC, NO x , CO purification performance and OSC thermal stability after high temperature durability.
  • An object of the present invention is to provide an exhaust gas purification catalyst material and an exhaust gas purification catalyst composition that have high exhaust gas purification performance after high-temperature durability and are excellent in heat resistance.
  • the present invention is based on the above findings and provides an exhaust gas catalyst material comprising a composite oxide represented by the formula (I).
  • M 1 MnO 3 (I) (In the formula, M 1 represents a rare earth element selected from Gd, Tb, Dy, Ho, Er, Tm, Yb and Lu.)
  • the present invention also provides an exhaust gas purifying catalyst composition containing the composite oxide and a catalytically active component.
  • the present invention also provides an exhaust gas purifying catalyst composition containing the composite oxide and containing no catalytic active component.
  • the present invention also provides an exhaust gas purification catalyst having a base material and a layer of the composition formed on the surface of the base material.
  • FIG. 1 is an X-ray diffraction chart of Example 3, Comparative Example 2 and Comparative Example 3 before thermal endurance.
  • FIG. 2 is a graph showing the purification performance of Example 1, Example 2 and Comparative Example 4 when the exhaust gas temperature rises.
  • CO and C 3 H 6 (a) is the rise in temperature is a graph showing a change in the conversion rate that is converted to CO 2, (b) NO x with respect to the increase of the temperature converted into N 2 It is a graph which shows transition of the conversion rate.
  • 3 is an X-ray diffraction chart before and after thermal endurance in Example 3, Comparative Example 3 and Comparative Example 4.
  • FIG. 1 is an X-ray diffraction chart of Example 3, Comparative Example 2 and Comparative Example 3 before thermal endurance.
  • FIG. 2 is a graph showing the purification performance of Example 1, Example 2 and Comparative Example 4 when the exhaust gas temperature rises.
  • CO and C 3 H 6 (a) is the rise in temperature is a graph showing a change in the conversion rate that is converted to
  • the exhaust gas purifying catalyst material of the present embodiment is composed of a complex oxide represented by the formula (I).
  • the composite oxide represented by the formula (I) has, for example, a powder form.
  • M 1 MnO 3 (I) (In the formula, M 1 represents a rare earth element selected from Gd, Tb, Dy, Ho, Er, Tm, Yb and Lu.)
  • the exhaust gas purification catalyst material is a material contained in the exhaust gas purification catalyst, preferably an exhaust gas comprising a porous substrate and a catalyst layer formed on the surface of the porous substrate. It is the material contained in the catalyst layer in the purification catalyst.
  • One aspect of the exhaust gas purifying catalyst material of the present embodiment serves as a carrier for supporting a catalytic active component described later, and exhibits exhaust gas purifying catalytic performance by supporting the catalytic active component. Further, another aspect of the exhaust gas purifying catalyst material of the present embodiment exhibits the exhaust gas purifying catalyst performance by itself even when the catalytically active component is not contained.
  • the exhaust gas purifying catalyst composition is a composition constituting the exhaust gas purifying catalyst, and preferably comprises a porous substrate and a catalyst layer formed on the surface of the porous substrate. It is the composition which comprises the catalyst layer in the catalyst for exhaust gas purification containing.
  • One aspect of the exhaust gas purifying catalyst composition of the present embodiment includes the composite oxide represented by the formula (I) and a catalytically active component described later. Further, another aspect of the exhaust gas purifying catalyst composition of the present embodiment is one that contains the composite oxide represented by the formula (I) but does not contain a catalytically active component described later.
  • Formula (I) is a composition formula, and a complex oxide composed of M 1 and Mn is represented by M 1 MnO 3 .
  • the molar ratio of M 1 and Mn in the composite oxide represented by the formula (I) is not strictly required to be 1: 1, and the ratio of the content (mole) of M 1 to the content (mole) of Mn. (M 1 / Mn) may vary, for example, in the range of 0.8 to 1.2, and preferably in the range of 0.9 to 1.2. That is, the complex oxide represented by the formula (I) can also be represented as M 1x MnO z . x is 0.8 or more and 1.2 or less.
  • the composite oxide represented by the formula (I) is preferably a composite oxide composed only of M1 and Mn.
  • the composition analysis can be performed, for example, by fluorescent X-ray analysis (XRF) or ICP emission spectroscopic analysis, and specifically by the method described in Examples described later.
  • the element represented by M 1, Gd, Tb, Dy , Ho, Er, Tm, at least one rare earth element selected from Yb, and Lu may be a type, a a combination of two or more May be.
  • Ho, Er, Tm, Yb, and Lu are preferable, and Er, Tm, Yb, and Lu are more preferable.
  • Yes most preferably Yb. Since Yb facilitates Mn oxidation-reduction, the composite oxide itself has an exhaust gas purification performance.
  • the crystal structure of the composite oxide represented by the formula (I) is preferably a hexagonal crystal structure.
  • OSC the material for exhaust gas purification catalyst and the catalyst composition for exhaust gas purification of the present invention are compared with the case of using a complex oxide represented by YbFeO 3 whose orthorhombic crystal is a stable phase shown in Comparative Example 2 described later.
  • OSC especially OSC after heat endurance is excellent. It is confirmed by X-ray diffraction measurement that the complex oxide has a hexagonal crystal structure.
  • the complex oxide represented by the formula (I) has a hexagonal crystal structure. It can be said that it has.
  • the composite oxide represented by the formula (I) has higher crystal structure stability to heat than the composite oxide described in Patent Document 1. Specifically, after heat endurance, the change from a hexagonal crystal to a crystal structure other than hexagonal is suppressed, and the crystal already has a hexagonal crystal structure before heat endurance. The degree of growth is relatively suppressed. Accordingly, the inventor has obtained the exhaust gas purification catalyst material of the present invention comprising the composite oxide represented by the formula (I) and the exhaust gas purification catalyst composition of the present invention containing the composite oxide after thermal endurance. Also believes that OSC is high. Further, such heat resistance is presumed to be a factor that the exhaust gas purification catalyst material and the exhaust gas purification catalyst composition of the present invention have high exhaust gas purification performance even after thermal endurance.
  • the composite oxide YbFe x Mn 1-x O 3 described in Patent Document 1 has a crystallinity even if it has a hexagonal crystal structure before thermal endurance. Is often low, and crystal growth tends to occur violently after thermal endurance. The inventor believes that this crystal growth causes a disadvantage in the exhaust gas purification performance because it causes a decrease in specific surface area accompanying an increase in the particle size of the composite oxide.
  • the term “heat durability” as used herein means a treatment that is exposed to a high temperature for a long time. For example, heating in air at 950 ° C. for 10 hours is preferable.
  • the composite oxide represented by the formula (I) is subjected to X-ray diffraction measurement using CuK ⁇ rays as a radiation source after heat durability treatment at 950 ° C. for 10 hours in air and before heat durability treatment. It is preferable that a peak pattern derived from the above hexagonal crystal is observed.
  • a peak pattern other than the hexagonal crystal may not be observed or may be observed after the heat durability treatment under the above conditions and before the heat durability treatment.
  • Yb is used as M1
  • a peak derived from YbMn 2 O 5 may be observed.
  • the complex oxide has a hexagonal crystal structure as a main crystal structure.
  • Whether or not it is the main crystal structure depends on whether the maximum intensity of the peak derived from the hexagonal crystal among the peaks observed in the X-ray diffraction measurement using CuK ⁇ rays as the radiation source Judgment can be made based on whether the intensity is greater than the maximum intensity of the peak.
  • the composite oxide represented by the formula (I) having a hexagonal crystal structure preferably has a crystallite diameter of the hexagonal crystal structure of 25 nm or more, reflecting the high crystallinity. More preferably, it is particularly preferably 35 nm or more.
  • the crystallite diameter of the hexagonal crystal structure of the composite oxide represented by the formula (I) is preferably 100 nm or less from the viewpoint of increasing the specific surface area, and more preferably 50 nm or less.
  • the crystallite size of the hexagonal crystal structure of the composite oxide represented by the formula (I) is calculated by the Scherrer formula defined by the following formula (1) using a powder X-ray diffraction method.
  • D k ⁇ ⁇ / ⁇ ⁇ cos ⁇ (1) here, D: Crystallite diameter (nm)
  • wavelength of measured X-ray (nm)
  • Half width of the diffraction line (radians)
  • Bragg angle of the diffraction line (radians)
  • X-ray diffraction measurement is preferably performed at 10 to 70 °, and the target of measurement may be a composite oxide or a composite oxide carrying a catalytically active component. X-ray diffraction measurement is performed, for example, by the method described in the examples.
  • the specific surface area of the composite oxide represented by the formula (I) is 3 m 2 / g or more, and it is easy to obtain a desired amount of the catalytically active component, and high exhaust gas purification activity can be obtained even under high space velocity conditions. It is preferable at a point, and it is preferable that it is 20 m ⁇ 2 > / g or less at the point which is hard to generate
  • the specific surface area of the composite oxide is more preferably 5 m 2 / g or more and 15 m 2 / g or less. As described above, the composite oxide reflects the stability of its crystal structure, and also has a high retention rate of the specific surface area after thermal durability.
  • the specific surface area of the composite oxide is preferably within the above range even after heat durability of 950 ° C. or higher.
  • the specific surface area of the composite oxide can be measured with the composite oxide or the composite oxide supporting a catalytically active component.
  • the specific surface area is measured by the BET multipoint method, and specifically can be measured by the method of Examples described later.
  • the composite oxide represented by the formula (I) can be produced, for example, by a coprecipitation method.
  • the complex oxide described in Patent Document 1 tends to generate impurities when it is produced by a coprecipitation method, and therefore, it is necessary to produce the complex oxide by a method having a complicated production process such as a solvothermal method.
  • the complex oxide of the present invention has an advantage that a stable quality can be obtained by a simple coprecipitation method.
  • the co-precipitation method by adding a precipitant to a solution comprising a water soluble salt and a manganese compound of a rare earth element M 1 as the starting material, after obtaining a precipitate, which was dried, expression by calcining (I And a method of obtaining a composite oxide represented by Examples of the water-soluble salts of rare earth elements M 1, nitrates and oxalates, acetates, ammine complex, chloride and the like.
  • Examples of manganese compounds include manganese nitrates, oxalates, acetates, ammine complex salts, and chlorides.
  • the precipitating agent include alkaline agents such as aqueous ammonia.
  • the solvent for the solution containing a water-soluble salt and manganese compound of a rare earth element M 1 include water.
  • a preferred addition amount of the precipitating agent is preferably 3 mol to 30 mol, and more preferably 5 mol to 15 mol with respect to 1 mol of the rare earth element M 1 .
  • the firing temperature is preferably 800 to 1000 ° C., more preferably 800 to 950 ° C., from the viewpoint of successfully obtaining the desired product.
  • the firing atmosphere is preferably air.
  • the composite oxide represented by the formula (I) is not limited to a product produced by a specific production method, and can also be produced by a solvothermal method and a complex polymerization method. As a procedure of the solvothermal method and the complex polymerization method, the method described in Patent Document 1 may be applied.
  • the composite oxide represented by the formula (I) can carry a catalytically active component.
  • the supported catalytically active component is preferably at least one selected from Pd, Rh, Pt, Ru and Ir. Only one type of catalytically active component may be used, or two or more types may be used in combination.
  • the catalytically active component may be in a metal state or an oxide state in the composite oxide.
  • the catalytically active component is at least one selected from Pd and Rh with respect to the composite oxide represented by the formula (I) from the viewpoint of dramatically improving the purification activity of the composite oxide in a very small amount. Preferably, it is Pd.
  • the phrase “catalytically active component is supported on the composite oxide” means that the composite oxide is physically, chemically adsorbed, bonded or held on the outer surface or the inner surface of the pores. Specifically, it can be confirmed that the composite oxide supports the catalytically active component by measuring the particle diameter when observed with, for example, a scanning electron microscope (SEM).
  • SEM scanning electron microscope
  • the average particle size of the catalytically active component present on the surface of the composite oxide is preferably 10% or less, more preferably 3% or less with respect to the average particle size of the composite oxide. It is preferably 1% or less.
  • the average particle diameter here is the average value of the particle diameters of 30 or more complex oxides and catalytic active components when observed with an SEM.
  • the amount of the catalytically active component supported on the composite oxide is preferably 0.01% by mass or more with respect to 100% by mass of the composite oxide from the viewpoint that the catalytic activity at a low temperature is more easily obtained.
  • the amount of the catalytically active component is preferably 10% by mass or less with respect to 100% by mass of the composite oxide represented by the formula (I) from the viewpoint of keeping costs low.
  • the amount of the catalytically active component is more preferably 0.01% by mass or more and 5% by mass or less, more preferably 0.05% by mass with respect to 100% by mass of the composite oxide represented by the formula (I).
  • the content is 2% by mass or less.
  • the amount of the catalytically active component in the exhaust gas purification catalyst composition is preferably 0.005% by mass or more and 8% by mass or less, and 0.01% by mass or more and 5% by mass or less. More preferably, it is 0.05 mass% or more and 2 mass% or less.
  • the composite oxide In order to support the catalytically active component on the composite oxide, it is preferable to immerse the composite oxide in the catalytically active component-containing solution, and then dry and calcinate.
  • the noble metal salt used for the preparation of the catalytically active component solution for example, acetate, nitrate, ammine complex salt, chloride and the like can be used.
  • the solvent water, acetone or the like can be used. Firing is preferably performed at 400 ° C. to 600 ° C. for 30 minutes to 10 hours in an air atmosphere.
  • the amount of the catalytically active component relative to the composite oxide is determined by the amount of noble metals such as Pt, Pd, Rh, Ru, and Ir in the solution obtained by dissolving the composite oxide material carrying the catalytically active component with an alkali or the like, and Mn. and obtained by measuring the amount of the rare earth element M 1 by ICP emission spectrometry.
  • noble metals such as Pt, Pd, Rh, Ru, and Ir
  • the composite oxide obtained by supporting the composite oxide represented by the formula (I) or the catalytically active component is an exhaust gas purification catalyst utilizing its excellent thermal stability such as OSC and the exhaust gas purification performance after high temperature durability.
  • an exhaust gas purification catalyst having a base material and an exhaust gas purification catalyst layer formed on the surface of the base material
  • the composite oxide particularly preferably the composite oxide carrying a catalytically active component on the exhaust gas purification catalyst layer
  • an exhaust gas purification catalyst having excellent heat resistance and exhaust gas purification performance at a low temperature can be obtained.
  • the shape of the substrate is not particularly limited, but is generally a shape of a flow-through type honeycomb, a plate, a pellet, or a wall-through type honeycomb, and preferably a flow-through type honeycomb. Or a wall-through type honeycomb.
  • the material of the base material include alumina (Al 2 O 3 ), mullite (3Al 2 O 3 -2SiO 2 ), cordierite (2MgO-2Al 2 O 3 -5SiO 2 ), and aluminum titanate. Examples thereof include ceramics such as (Al 2 TiO 5 ) and silicon carbide (SiC), and metal materials such as stainless steel.
  • the exhaust gas-purifying catalyst composition constituting the exhaust gas-purifying catalyst layer may be composed of, for example, the composite oxide represented by the formula (I) or the composite oxide carrying a catalytically active component. You may contain components other than. Examples of the components other than the composite oxide in the exhaust gas purification catalyst composition constituting the exhaust gas purification catalyst layer include, for example, TiO 2 , SiO 2 , zeolite, MgO, MgAl 2 , mainly serving as a carrier.
  • an inorganic porous material such as O 4
  • an OSC material such as CeO 2 , CeO 2 —ZrO 2 composite oxide, and the like serving as a NO x adsorbent, Ba, Sr
  • the alkaline earth metal compound such as Mg and those serving as a binder
  • the catalytically active component exemplified above is supported.
  • the amount of the composite oxide represented by the formula (I) is not limited, but is preferably 10% by mass or more and 99.9% by mass or less, for example, 20% by mass or more and 98% by mass or less. It is more preferable that it is 40 mass% or more and 95 mass% or less.
  • the amount of the inorganic porous material including the composite oxide represented by the formula (I) is 10 mass% or more in the exhaust gas purification catalyst composition from the viewpoint of obtaining heat resistance and low temperature exhaust gas purification performance according to the present invention. It is preferably 9% by mass or less, more preferably 20% by mass or more and 98% by mass or less, and particularly preferably 40% by mass or more and 95% by mass or less.
  • the amount of the OSC material including the composite oxide represented by the formula (I) is OSC, heat resistance, and low temperature exhaust gas purification performance.
  • it is preferably 10% by mass or more and 80% by mass or less, more preferably 20% by mass or more and 70% by mass or less, and more preferably 40% by mass or more and 60% by mass or less in the exhaust gas purification catalyst composition. It is particularly preferable that the content is not more than mass%.
  • the alkaline earth metal compounds include oxides and carbonates of alkaline earth metals, as its amount, taking into consideration the the NO x adsorption properties, the balance of exhaust gas purification performance in heat resistance and low temperature, the exhaust gas It is preferable that it is 10 mass% or less in the catalyst composition for purification, and it is more preferable that it is 1 mass% or more and 5 mass% or less.
  • Exhaust gas purification in which a catalyst layer is formed on a base material by applying a slurry having the exhaust gas purification catalyst composition containing the composite oxide represented by the formula (I) to the surface of the base material, drying, and firing.
  • the catalyst for use can be obtained.
  • the composite oxide represented by the above formula (I) and, if necessary, the other components described above are treated with catalytic activity.
  • a slurry containing an exhaust gas purification catalyst composition is prepared by adding it to an aqueous solution containing a water-soluble salt of the component, and this slurry is applied to a substrate, dried and fired to form an exhaust gas purification catalyst.
  • the solid content of the slurry is preferably 20% by mass or more and 40% by mass or less from the viewpoint of workability when forming the exhaust gas purifying catalyst.
  • a slurry may be prepared without using an aqueous solution containing the water-soluble salt of the catalytically active component described above.
  • the temperature for firing the substrate coated with the slurry is preferably 300 ° C. to 800 ° C., more preferably 400 ° C. to 600 ° C., and the firing time is 0 5 hours to 10 hours are preferred, and 1 hour to 3 hours are more preferred. Firing can be performed in an air atmosphere.
  • the amount of the exhaust gas purification catalyst composition of the present invention is preferably 60 g / L or more from the viewpoint of obtaining heat resistance and low temperature exhaust gas purification performance according to the present invention, and 160 g / L or less. It is preferable from the point that suitable low-temperature activity can be obtained while preventing a decrease in back pressure. From these viewpoints, in the exhaust gas purification catalyst of the present invention, the amount of the exhaust gas purification catalyst composition of the present invention is more preferably from 70 g / L to 140 g / L, more preferably from 85 g / L to 120 g / L.
  • the amount of the exhaust gas-purifying catalyst composition in the exhaust gas-purifying catalyst is an amount based on the volume of the substrate including the volume of the pores of the porous substrate.
  • the preferable amount of the composite oxide represented by the formula (I) in the exhaust gas purification catalyst may be the same amount as the preferable amount of the exhaust gas purification catalyst composition of the present invention in the exhaust gas purification catalyst. .
  • the exhaust gas purifying catalyst material, the exhaust gas purifying catalyst composition, and the exhaust gas purifying catalyst of the present embodiment have stable exhaust gas purifying catalyst performance even when exposed to a high temperature of, for example, about 900 ° C. to 1150 ° C.
  • the exhaust gas purification performance at a low temperature can be shown.
  • Such an exhaust gas purification catalyst material, an exhaust gas purification catalyst composition, and an exhaust gas purification catalyst are stable and high exhaust gas purification performance as an exhaust gas purification material of an internal combustion engine using a fossil fuel as a power source such as a gasoline engine or a diesel engine. Can be demonstrated.
  • the exhaust gas purifying catalyst material, the exhaust gas purifying catalyst composition, and the exhaust gas purifying catalyst of the present embodiment are used for purifying exhaust gas discharged from gasoline engines such as automobiles and motorcycles because of their high heat resistance. Is preferred.
  • Example 1 Ytterbium nitrate n-hydrate (manufactured by Wako Pure Chemical Industries, Ltd.) is used as the ytterbium compound, manganese nitrate hexahydrate (manufactured by Wako Pure Chemical Industries, Ltd.) is used as the manganese compound, and 28% by mass ammonia water (Japanese Kogure Pharmaceutical Co., Ltd.) was used.
  • a coprecipitate was 1: 1: 10.
  • the mixture was stirred at room temperature (25 ° C.) for about 1 hour, followed by standing aging for 1 hour, and the coprecipitate was separated by filtration.
  • YbMnO 3 powder thus obtained was subjected to composition analysis by XRF under the following conditions, the molar ratio of M 1 for Mn (M 1 / Mn) was 1.03.
  • ⁇ Composition analysis by XRF> The calibration curve method was adopted as the quantitative method.
  • ZSX Primus II manufactured by Rigaku Corporation was used as a measuring instrument.
  • the measurement sample was prepared as follows. The YbMnO 3 powder was pulverized to 20 ⁇ m or less (D50) using a disk mill (Retsch RS200), and then 1 g of the pulverized powder was molded into a disk shape with a pressure molding machine and measured.
  • Example 2 To the acetone solution in which palladium acetate was dissolved, the YbMnO 3 powder produced in Example 1 was added and stirred to obtain a slurry. After the acetone solution was evaporated to dryness, the obtained powder was calcined at 500 ° C. for 30 minutes in the air to produce YbMnO 3 powder supporting Pd. The amount of Pd was 0.1% by mass with respect to 100% by mass of YbMnO 3 .
  • YbMnO 3 which Pd is supported as Pd / YbMnO 3.
  • Example 3 The amount of Pd / YbMnO 3 powder in which the amount of Pd was 1% by mass relative to 100% by mass of YbMnO 3 was manufactured by changing the amount of palladium acetate in acetone.
  • the production conditions other than the addition amount of palladium acetate in acetone were the same as in Example 2.
  • FIG. 1 shows an X-ray diffraction chart measured by the X-ray diffraction measurement method under the following conditions in the as-manufactured state of this Pd / YbMnO 3 powder.
  • the obtained Pd / YbMnO 3 powder has a peak pattern derived from a hexagonal crystal of YbMnO 3 . Based on the obtained X-ray diffraction measurement result, the crystallite diameter of the hexagonal crystal structure was measured by the above calculation method, and found to be 28 nm.
  • Example 4 Pd / YbMnO 3 powder having a Pd content of 2% by mass with respect to 100% by mass of YbMnO 3 was produced by changing the amount of palladium acetate in acetone.
  • the production conditions other than the addition amount of palladium acetate in acetone were the same as in Example 2.
  • This suspension was transferred to an autoclave reaction tube, charged into an autoclave (300 mL), and 30 ml of 1,4-BG was also added to the gap. After the inside of the autoclave was purged with nitrogen, the temperature was raised from room temperature to 315 ° C. at 2.3 ° C./min and reacted for 2 hours. The product was washed with methanol and dried. Thereafter, it was crushed and fired at 500 ° C. for 30 minutes in an air atmosphere to obtain YbFe 0.6 Mn 0.4 O 3 powder.
  • CeO 2 —ZrO 2 solid solution material (CeO 2 —ZrO 2 material) having a CeO 2 content of 40% by mass was prepared.
  • a CeO 2 —ZrO 2 material was added to a 1% by mass palladium nitrate aqueous solution and stirred to obtain a slurry. This slurry was fired under air at 500 ° C. for 2 hours to produce a Pd / CeO 2 —ZrO 2 material powder.
  • the amount of Pd was 1% by mass with respect to 100% by mass of CeO 2 —ZrO 2 .
  • the powder obtained in Examples and Comparative Examples was subjected to the following evaluation.
  • the powders obtained in Examples and Comparative Examples are also referred to as exhaust gas purification catalyst compositions.
  • Simulated exhaust gas (composition is volume ratio): C 3 H 6 : 250 ppm, CO: 1000 ppm, CO 2 : 0%, O 2 : 1125 ppm, NO: 1000 ppm, H 2 O: 0%, and He balance T50 before firing under test condition 1 (also referred to as “T50 500 ° C ⁇ 30 minutes” from “500 ° C. ⁇ 30 minutes” in manufacturing conditions) and T50 950 after firing at endurance test condition 1 at 950 ° C. for 30 minutes.
  • the exhaust gas purification catalyst composition of Example 3 has a general durability temperature required for an exhaust gas purification catalyst for gasoline vehicles, as compared with Comparative Example 1 using YMnO 3 powder as a carrier. It can be seen that even after endurance at 950 ° C., the NO x , HC, and CO purification performance at low temperatures is excellent. Further, it can be seen that the exhaust gas purification catalyst composition of Example 3 hardly deteriorates due to durability compared with Comparative Example 1, and the exhaust gas purification performance after durability is very high.
  • ⁇ Endurance test condition 2> The exhaust gas purifying catalyst compositions prepared in Examples 2 to 4 and Comparative Examples 2 to 4 were subjected to durable firing at 950 ° C. for 10 hours in an air atmosphere.
  • ⁇ Evaluation 2 NO x , HC, CO purification performance before and after endurance test 2> Regarding the exhaust gas purifying catalyst compositions of Examples 2 to 4 and Comparative Examples 2 to 4 before and after firing under the durability test condition 2, NO x , HC and CO purification performance was evaluated using an atmospheric pressure fixed bed flow type reactor. .
  • the evaluation method of T50 before and after firing is the same as in Evaluation 1.
  • the exhaust gas purifying catalyst compositions of Examples 2 to 4 were compared with Comparative Examples 2 to 4 using YbFeO 3 powder, YbFe 0.6 Mn 0.4 O 3 powder, and alumina powder, respectively, as carriers. It can be seen that even after endurance at 950 ° C., which is a general endurance temperature required for exhaust gas purification catalysts for gasoline vehicles, it is excellent in NO x , HC and CO purification performance at low temperatures. In addition, it can be seen that the exhaust gas purification catalyst compositions of Examples 2 to 4 hardly deteriorate due to durability compared to Comparative Examples 2 to 4, and the exhaust gas purification performance after durability is very high.
  • the exhaust gas purification catalyst composition of Example 3 using YbMnO 3 powder has a higher OSC ability after high temperature durability than the general exhaust gas purification catalyst composition of Comparative Example 5. It can be seen that the heat resistance is high. Further, even in Example 2 in which the amount of Pd supported is 1/10 of Example 3, it can be seen that the OSC ability after high-temperature durability is high and the heat resistance is high.
  • the exhaust gas purifying catalyst composition of Example 1 has an exhaust gas purifying catalytic activity even when it does not contain a catalytic active component, and the amount of catalytic active component is 0 as in Example 2. It can be seen that even when the amount is as small as 1% by mass, the catalyst of the exhaust gas purification catalyst activity is superior to that of the composition of Comparative Example 4 in which 1% by mass of the catalytically active component is supported. Therefore, by using the composite oxide of the present invention, it is possible to achieve both reduction in the amount of noble metal used and improvement in exhaust gas purification catalyst performance.
  • ⁇ Evaluation 5 Heat resistance of crystal structure>
  • the X-ray diffraction charts measured for the exhaust gas purifying catalyst compositions of Example 3, Comparative Example 3, and Comparative Example 4 before and after the durability test of ⁇ Durability Test Condition 2> (hereinafter also simply referred to as Durability Test 2) are shown in the figure. 3 shows. The above conditions were adopted for the X-ray diffraction measurement method.
  • ⁇ Method for measuring specific surface area> The specific surface area was measured by BET multipoint method (measurement gas: nitrogen) using BEL SORP-mini II-HSP manufactured by Microtrack Bell.
  • the Pd / YbMnO 3 powder of Example 3 had a peak pattern derived from the hexagonal YbMnO 3 before and after the endurance test 2, and before and after the endurance test of ⁇ endurance test condition 2>. However, there is almost no change in the peak pattern, and the crystal structure at the time of manufacture is maintained after the endurance. On the other hand, Pd / YbFe 0.6 Mn 0.4 O 3 of Comparative Example 3 has a very sharp peak after the durability test 2 and the crystal structure is greatly changed. To confirm this, as shown in Table 4, the retention rate after endurance of the specific surface area of Example 3 was as high as 69.2%, whereas in Comparative Example 3, the retention rate after endurance of the specific surface area was 12%.
  • an exhaust gas purification catalyst material an exhaust gas purification catalyst composition, and an exhaust gas purification catalyst that have high exhaust gas purification performance after endurance at high temperatures and are excellent in heat resistance.

Abstract

This material for an exhaust gas purification catalyst comprises the complex oxide indicated by formula (I). This catalyst composition for exhaust gas purification includes said complex oxide and a catalytic activity component. Formula (I): M1MnO3 (In this formula, M1 indicates at least one type of rare earth element selected from Gd, Tb, Dy, Ho, Er, Tm, Yb, and Lu). M1 in formula (I) is preferably a rare earth element selected from Er, Tm, Yb, and Lu. The crystal structure of the complex oxide indicated by formula (I) is preferably a hexagonal structure.

Description

排ガス浄化触媒用材料及び排ガス浄化用触媒組成物並びに排ガス浄化触媒Exhaust gas purification catalyst material, exhaust gas purification catalyst composition, and exhaust gas purification catalyst
 本発明は希土類元素とマンガンを含む複合酸化物からなる排ガス浄化触媒用材料、該複合酸化物を含有する排ガス浄化用触媒組成物、並びに該排ガス浄化用触媒組成物を含む排ガス浄化触媒に関する。 The present invention relates to an exhaust gas purification catalyst material comprising a complex oxide containing rare earth elements and manganese, an exhaust gas purification catalyst composition containing the complex oxide, and an exhaust gas purification catalyst comprising the exhaust gas purification catalyst composition.
 自動車やバイク(鞍乗型車両ともいう)等のガソリンエンジンやディーゼルエンジン等の内燃機関から排出される排ガス中には炭化水素(HC)、一酸化炭素(CO)、窒素酸化物(NO)等の有害成分が含まれている。従来、これらの有害成分を浄化して無害化する目的で三元触媒が用いられている。このような三元触媒として、白金(Pt)、パラジウム(Pd)、ロジウム(Rh)等のコスト高の要因となる貴金属と、アルミナ、セリア、ジルコニア又はこれらの複合酸化物とを任意に組み合わせたものが使用されている。 Hydrocarbon (HC), carbon monoxide (CO), and nitrogen oxide (NO x ) are contained in exhaust gas emitted from internal combustion engines such as automobiles and motorcycles (also referred to as saddle-type vehicles) such as gasoline engines and diesel engines. Contains harmful ingredients such as. Conventionally, a three-way catalyst has been used for the purpose of purifying and detoxifying these harmful components. As such a three-way catalyst, a noble metal that causes high costs such as platinum (Pt), palladium (Pd), rhodium (Rh), and alumina, ceria, zirconia, or a composite oxide thereof is arbitrarily combined. Things are used.
 またYbFeMn1-xを担体とし、これに触媒活性成分を担持させた排気浄化用触媒が報告されている(特許文献1)。同文献には、YbFeMn1-xを担体とする排気浄化用触媒は、従来よりも貴金属量を減らしても低温域での排ガス浄化作用が高い旨が記載されている。
 更にYMnOを担体とし、これに触媒活性成分を担持させた排気浄化用触媒が報告されている(特許文献2)。同文献には、YMnOを担体とする排気浄化用触媒について低温域での排ガス浄化作用が高い旨が記載されている。
Further, an exhaust purification catalyst in which YbFe x Mn 1-x O 3 is used as a carrier and a catalytically active component is carried on this carrier has been reported (Patent Document 1). This document describes that an exhaust gas purification catalyst using YbFe x Mn 1-x O 3 as a carrier has a high exhaust gas purification effect in a low temperature range even if the amount of noble metal is reduced as compared with the conventional art.
Further, an exhaust purification catalyst in which YMnO 3 is used as a carrier and a catalytically active component is supported thereon has been reported (Patent Document 2). This document describes that an exhaust gas purification catalyst using YMnO 3 as a carrier has a high exhaust gas purification effect in a low temperature range.
WO2016/148062号パンフレットWO2016 / 148062 pamphlet 特開2011-189306号公報JP 2011-189306 A
 近年、浄化効率向上のためエンジン始動時から浄化性を発揮することだけでなく、それを維持することが益々求められている。つまり、低温での排ガス浄化触媒活性すなわちライトオフ性能のみならず、高温の排ガスに長時間さらされても、低温域での排ガス浄化触媒活性を維持できる高温耐久性が益々求められている。この点に関し、特許文献1に記載されたYbFeMn1-xに触媒活性成分を担持した触媒組成物は、高温耐久後のHC、NO、CO浄化性能の点で改善の余地があった。またこの触媒組成物はOSC(oxygen storage capacity)の熱的安定性という点でも、改善の余地があった。
 また、特許文献2に記載の触媒組成物も、高温耐久後のHC、NO、CO浄化性能及びOSCの熱的安定性は十分なものではなかった。
In recent years, in order to improve the purification efficiency, it has been increasingly demanded not only to exhibit the purification performance from the start of the engine but also to maintain it. That is, not only the exhaust gas purification catalyst activity at low temperature, that is, the light-off performance, but also high temperature durability that can maintain the exhaust gas purification catalyst activity in the low temperature range even when exposed to high temperature exhaust gas for a long time is increasingly required. In this regard, the catalyst composition in which the catalytically active component is supported on YbFe x Mn 1-x O 3 described in Patent Document 1 has room for improvement in terms of HC, NO x , and CO purification performance after high-temperature durability. there were. Further, this catalyst composition has room for improvement in terms of thermal stability of OSC (oxygen storage capacity).
Further, the catalyst composition described in Patent Document 2 also has insufficient HC, NO x , CO purification performance and OSC thermal stability after high temperature durability.
 本発明の課題は、高温耐久後の排ガス浄化性能が高く、耐熱性に優れた排ガス浄化触媒用材料及び排ガス浄化用触媒組成物を提供することにある。 An object of the present invention is to provide an exhaust gas purification catalyst material and an exhaust gas purification catalyst composition that have high exhaust gas purification performance after high-temperature durability and are excellent in heat resistance.
 本発明者は、鋭意検討したところ、驚くべきことに、Feを非含有の特定の希土類マンガン酸化物が、従来得難かった、高温耐久後の高い排ガス浄化性能及び高温耐久後の高いOSCを有することを見出した。 As a result of intensive studies, the present inventors have surprisingly found that a specific rare earth manganese oxide not containing Fe has high exhaust gas purification performance after high temperature durability and high OSC after high temperature durability, which has been difficult to obtain conventionally. I found out.
 本発明は、上記知見に基づくものであり、式(I)で示される複合酸化物からなる排ガス触媒用材料を提供するものである。
 MMnO・・・(I)
(式中、MはGd、Tb、Dy、Ho、Er、Tm、Yb及びLuから選ばれる希土類元素を示す。)
The present invention is based on the above findings and provides an exhaust gas catalyst material comprising a composite oxide represented by the formula (I).
M 1 MnO 3 (I)
(In the formula, M 1 represents a rare earth element selected from Gd, Tb, Dy, Ho, Er, Tm, Yb and Lu.)
 また本発明は、前記複合酸化物及び触媒活性成分を含有する排ガス浄化用触媒組成物を提供するものである。 The present invention also provides an exhaust gas purifying catalyst composition containing the composite oxide and a catalytically active component.
 また本発明は、前記複合酸化物を含有し、触媒活性成分を含有しない排ガス浄化用触媒組成物を提供するものである。 The present invention also provides an exhaust gas purifying catalyst composition containing the composite oxide and containing no catalytic active component.
 また本発明は、基材と、当該基材表面に形成された前記組成物の層とを有する排ガス浄化触媒を提供するものである。 The present invention also provides an exhaust gas purification catalyst having a base material and a layer of the composition formed on the surface of the base material.
図1は、実施例3、比較例2及び比較例3の熱耐久前のX線回折チャートである。1 is an X-ray diffraction chart of Example 3, Comparative Example 2 and Comparative Example 3 before thermal endurance. 図2は、排ガス昇温時における実施例1、実施例2及び比較例4の浄化性能を示すグラフである。(a)が温度の上昇に対してCO及びCがCOに転化される転化率の推移を示すグラフであり、(b)が温度の上昇に対してNOがNに転化される転化率の推移を示すグラフである。FIG. 2 is a graph showing the purification performance of Example 1, Example 2 and Comparative Example 4 when the exhaust gas temperature rises. CO and C 3 H 6 (a) is the rise in temperature is a graph showing a change in the conversion rate that is converted to CO 2, (b) NO x with respect to the increase of the temperature converted into N 2 It is a graph which shows transition of the conversion rate. 図3は、実施例3、比較例3及び比較例4の熱耐久前後のX線回折チャートである。3 is an X-ray diffraction chart before and after thermal endurance in Example 3, Comparative Example 3 and Comparative Example 4. FIG.
 以下本発明を、その好ましい実施形態に基づき説明する。
 本実施形態の排ガス浄化触媒用材料は、式(I)で示される複合酸化物からなる。式(I)で示される複合酸化物は、例えば、粉末状の形態を有していている。
 MMnO・・・(I)
(式中、MはGd、Tb、Dy、Ho、Er、Tm、Yb及びLuから選ばれる希土類元素を示す。)
Hereinafter, the present invention will be described based on preferred embodiments thereof.
The exhaust gas purifying catalyst material of the present embodiment is composed of a complex oxide represented by the formula (I). The composite oxide represented by the formula (I) has, for example, a powder form.
M 1 MnO 3 (I)
(In the formula, M 1 represents a rare earth element selected from Gd, Tb, Dy, Ho, Er, Tm, Yb and Lu.)
 本明細書中、排ガス浄化触媒用材料とは、排ガス浄化触媒に含まれる材料のことであり、好ましくは、多孔質基材と、多孔質基材の表面に形成される触媒層とを含む排ガス浄化触媒における触媒層に含まれる材料のことである。
 本実施形態の排ガス浄化触媒用材料の一態様は、後述する触媒活性成分を担持する担体としての役割を果たし、触媒活性成分を担持することで排ガス浄化触媒性能を発揮するものである。
 また、本実施形態の排ガス浄化触媒用材料の別態様は、触媒活性成分が非含有であっても、それ自体で排ガス浄化触媒性能を発揮するものである。
In the present specification, the exhaust gas purification catalyst material is a material contained in the exhaust gas purification catalyst, preferably an exhaust gas comprising a porous substrate and a catalyst layer formed on the surface of the porous substrate. It is the material contained in the catalyst layer in the purification catalyst.
One aspect of the exhaust gas purifying catalyst material of the present embodiment serves as a carrier for supporting a catalytic active component described later, and exhibits exhaust gas purifying catalytic performance by supporting the catalytic active component.
Further, another aspect of the exhaust gas purifying catalyst material of the present embodiment exhibits the exhaust gas purifying catalyst performance by itself even when the catalytically active component is not contained.
 本明細書中、排ガス浄化用触媒組成物とは、排ガス浄化触媒を構成する組成物のことであり、好ましくは、多孔質基材と、多孔質基材の表面に形成される触媒層とを含む排ガス浄化用触媒における触媒層を構成する組成物のことである。
 本実施形態の排ガス浄化用触媒組成物の一態様は、式(I)で示される複合酸化物と後述する触媒活性成分とを含むものである。
 また、本実施形態の排ガス浄化用触媒組成物の別態様は、式(I)で示される複合酸化物を含むものの、後述する触媒活性成分を含有しないものである。
In the present specification, the exhaust gas purifying catalyst composition is a composition constituting the exhaust gas purifying catalyst, and preferably comprises a porous substrate and a catalyst layer formed on the surface of the porous substrate. It is the composition which comprises the catalyst layer in the catalyst for exhaust gas purification containing.
One aspect of the exhaust gas purifying catalyst composition of the present embodiment includes the composite oxide represented by the formula (I) and a catalytically active component described later.
Further, another aspect of the exhaust gas purifying catalyst composition of the present embodiment is one that contains the composite oxide represented by the formula (I) but does not contain a catalytically active component described later.
 式(I)は組成式でありM、Mnからなる複合酸化物のことをMMnOで示している。
 式(I)で示される複合酸化物におけるMとMnのモル比は厳密に1:1であることを要さず、Mnの含有量(モル)に対するMの含有量(モル)の比率(M/Mn)は、例えば0.8以上1.2以下の範囲、好ましくは0.9以上1.2以下の範囲で変動することがある。すなわち、式(I)で表される複合酸化物は、M1xMnOと表すこともできる。xは0.8以上1.2以下である。zは、M1の価数を3価と、Mnの価数を3価と、酸素の価数を2価とした場合に、化学量論組成となるように算出した値であり、(x×3+3)÷2と表すことができる。
 また、式(I)で示される複合酸化物は、M1とMnからのみ構成される複合酸化物であることが好ましいが、本発明による耐熱性及び低温での排ガス浄化性能が得られる範囲において、これら以外の元素を、M1とMnの合計モル数に対して、10モル%以下含有してもよい。
 組成分析は、例えば蛍光X線分析(XRF)やICP発光分光分析により行うことができ、具体的には後述する実施例に記載の方法にて行うことができる。
Formula (I) is a composition formula, and a complex oxide composed of M 1 and Mn is represented by M 1 MnO 3 .
The molar ratio of M 1 and Mn in the composite oxide represented by the formula (I) is not strictly required to be 1: 1, and the ratio of the content (mole) of M 1 to the content (mole) of Mn. (M 1 / Mn) may vary, for example, in the range of 0.8 to 1.2, and preferably in the range of 0.9 to 1.2. That is, the complex oxide represented by the formula (I) can also be represented as M 1x MnO z . x is 0.8 or more and 1.2 or less. z is a value calculated to have a stoichiometric composition when the valence of M1 is trivalent, the valence of Mn is trivalent, and the valence of oxygen is bivalent, and (xx 3 + 3) ÷ 2.
Further, the composite oxide represented by the formula (I) is preferably a composite oxide composed only of M1 and Mn. However, in the range where the heat resistance and the exhaust gas purification performance at low temperature according to the present invention are obtained, You may contain 10 mol% or less of elements other than these with respect to the total number of moles of M1 and Mn.
The composition analysis can be performed, for example, by fluorescent X-ray analysis (XRF) or ICP emission spectroscopic analysis, and specifically by the method described in Examples described later.
 Mで表される元素としては、Gd、Tb、Dy、Ho、Er、Tm、Yb及びLuから選ばれる少なくとも一種の希土類元素であり、一種であってもよく、二種以上の組み合わせであってもよい。これらの中でも、後述する六方晶の結晶構造が特に形成し易いイオン半径を備える観点から、好ましくは、Ho、Er、Tm、Yb及びLuであり、より好ましくは、Er、Tm、Yb及びLuであり、最も好ましくは、Ybである。YbはMnの酸化還元を容易にするため、複合酸化物自体としても排ガス浄化性能を備えたものとなる。 As the element represented by M 1, Gd, Tb, Dy , Ho, Er, Tm, at least one rare earth element selected from Yb, and Lu, may be a type, a a combination of two or more May be. Among these, from the viewpoint of providing an ionic radius in which the hexagonal crystal structure described below is particularly easy to form, Ho, Er, Tm, Yb, and Lu are preferable, and Er, Tm, Yb, and Lu are more preferable. Yes, most preferably Yb. Since Yb facilitates Mn oxidation-reduction, the composite oxide itself has an exhaust gas purification performance.
 式(I)で示される複合酸化物の結晶構造は、六方晶構造であることが好ましい。このような複合酸化物に触媒活性成分が担持されることで、より高いOSCを有することとなる。これにより本発明の排ガス浄化触媒用材料及び排ガス浄化用触媒組成物は、後述する比較例2に示す斜方晶が安定相であるYbFeOで示される複合酸化物を用いた場合に比べて、OSC、特に熱耐久後のOSCが優れたものとなる。複合酸化物が六方晶構造を有することはX線回折測定により確認される。例えばMとしてYbを用いた場合、線源としてCuKα線を用いた複合酸化物のX線回折測定において、2θ=32°以上34°以下、28°以上30°以下、及び14°以上17°以下の範囲にそれぞれ六方晶のYbMnO3の(112)面、(110)面、(002)面に由来するピークが観察された場合、式(I)で示される複合酸化物に、六方晶構造を有するといえる。 The crystal structure of the composite oxide represented by the formula (I) is preferably a hexagonal crystal structure. By supporting the catalytically active component on such a composite oxide, it has a higher OSC. Thereby, the material for exhaust gas purification catalyst and the catalyst composition for exhaust gas purification of the present invention are compared with the case of using a complex oxide represented by YbFeO 3 whose orthorhombic crystal is a stable phase shown in Comparative Example 2 described later. OSC, especially OSC after heat endurance is excellent. It is confirmed by X-ray diffraction measurement that the complex oxide has a hexagonal crystal structure. For example, when using a Yb as M 1, the X-ray diffraction measurement of the complex oxide using CuKα ray as a radiation source, 2 [Theta] = 32 ° or 34 ° or less, 28 ° or 30 ° or less, and 14 ° or 17 ° When peaks derived from the (112) plane, (110) plane, and (002) plane of hexagonal YbMnO 3 are observed in the following ranges, the complex oxide represented by the formula (I) has a hexagonal crystal structure. It can be said that it has.
 また本発明において、式(I)で示される複合酸化物は、特許文献1に記載の複合酸化物に比べて、結晶構造の熱に対する安定性が高いものとなる。具体的には、熱耐久後において、六方晶から六方晶以外の結晶構造への変化が抑制されたものとなるほか、熱耐久前に既に六方晶構造を有しており、熱耐久後における結晶成長の程度が比較的抑制されているものとなる。本発明者は、これにより、式(I)で示される複合酸化物からなる本発明の排ガス浄化触媒用材料及び当該複合酸化物を含む本発明の排ガス浄化用触媒組成物は、熱耐久後においてもOSCが高いと考えている。またこのような耐熱性は、本発明の排ガス浄化触媒用材料及び排ガス浄化用触媒組成物が熱耐久後においても高い排ガス浄化性能を有する一因であると推測される。これに対し、後述する比較例3に記載される通り、特許文献1に記載の複合酸化物YbFeMn1-xは、熱耐久前は六方晶構造を有していても、結晶性が低い場合が多く、熱耐久後に結晶成長が激しく起きる傾向にある。この結晶成長は、複合酸化物の粒子径の増大に伴う比表面積の低下を引き起こすため、排ガス浄化性能に不利益を与えるものと発明者は考えている。ここでいう熱耐久とは、長時間高温にさらす処理を意味し、例えば950℃、10時間、空気中における加熱が好ましく挙げられる。 In the present invention, the composite oxide represented by the formula (I) has higher crystal structure stability to heat than the composite oxide described in Patent Document 1. Specifically, after heat endurance, the change from a hexagonal crystal to a crystal structure other than hexagonal is suppressed, and the crystal already has a hexagonal crystal structure before heat endurance. The degree of growth is relatively suppressed. Accordingly, the inventor has obtained the exhaust gas purification catalyst material of the present invention comprising the composite oxide represented by the formula (I) and the exhaust gas purification catalyst composition of the present invention containing the composite oxide after thermal endurance. Also believes that OSC is high. Further, such heat resistance is presumed to be a factor that the exhaust gas purification catalyst material and the exhaust gas purification catalyst composition of the present invention have high exhaust gas purification performance even after thermal endurance. On the other hand, as described in Comparative Example 3 to be described later, the composite oxide YbFe x Mn 1-x O 3 described in Patent Document 1 has a crystallinity even if it has a hexagonal crystal structure before thermal endurance. Is often low, and crystal growth tends to occur violently after thermal endurance. The inventor believes that this crystal growth causes a disadvantage in the exhaust gas purification performance because it causes a decrease in specific surface area accompanying an increase in the particle size of the composite oxide. The term “heat durability” as used herein means a treatment that is exposed to a high temperature for a long time. For example, heating in air at 950 ° C. for 10 hours is preferable.
 例えば、式(I)で示される複合酸化物は、950℃で10時間、空気下で熱耐久処理した後及び熱耐久処理前のいずれにおいても、CuKα線を線源としたX線回折測定において、上述した六方晶に由来するピークパターンが観察されることが好ましい。
 また式(I)で示される複合酸化物は前記条件で熱耐久処理した後及び熱耐久処理前のいずれにおいても、六方晶以外のピークパターンが観察されなくてもよく、或いは観察されてもよい。例えばM1としてYbを用いた場合、YbMnに由来するピークが観察されてもよい。
 なお、六方晶以外のピークパターンが観察される場合、六方晶構造が主な結晶構造として複合酸化物に有することが好ましい。主な結晶構造であるか否かは、CuKα線を線源としたX線回折測定において観察されるピークのうち、六方晶に由来するピークの最大強度が、他の結晶構造に由来する全てのピークの最大強度よりも大きいか否かで判断することができる。
For example, the composite oxide represented by the formula (I) is subjected to X-ray diffraction measurement using CuKα rays as a radiation source after heat durability treatment at 950 ° C. for 10 hours in air and before heat durability treatment. It is preferable that a peak pattern derived from the above hexagonal crystal is observed.
In the composite oxide represented by the formula (I), a peak pattern other than the hexagonal crystal may not be observed or may be observed after the heat durability treatment under the above conditions and before the heat durability treatment. . For example, when Yb is used as M1, a peak derived from YbMn 2 O 5 may be observed.
When a peak pattern other than hexagonal is observed, it is preferable that the complex oxide has a hexagonal crystal structure as a main crystal structure. Whether or not it is the main crystal structure depends on whether the maximum intensity of the peak derived from the hexagonal crystal among the peaks observed in the X-ray diffraction measurement using CuKα rays as the radiation source Judgment can be made based on whether the intensity is greater than the maximum intensity of the peak.
 上記の通り六方晶構造を有する式(I)で示される複合酸化物は、その結晶性が高いことを反映して、六方晶構造の結晶子径が25nm以上であることが好ましく、30nm以上であることがより好ましく、35nm以上であることが特に好ましい。式(I)で示される複合酸化物の六方晶構造の結晶子径は100nm以下であることが、比表面積を高くする観点で好ましく、50nm以下であることがより好ましい。 As described above, the composite oxide represented by the formula (I) having a hexagonal crystal structure preferably has a crystallite diameter of the hexagonal crystal structure of 25 nm or more, reflecting the high crystallinity. More preferably, it is particularly preferably 35 nm or more. The crystallite diameter of the hexagonal crystal structure of the composite oxide represented by the formula (I) is preferably 100 nm or less from the viewpoint of increasing the specific surface area, and more preferably 50 nm or less.
 式(I)で示される複合酸化物の六方晶構造の結晶子径は、粉末X線回折法を用い、下記(1)式で定義されるシェラーの式により算出する。測定ピークは2θ=15°近傍を用いる。
D=k×λ/β×cosθ ・・・(1)
ここで、
D:結晶子径(nm)
k:定数(測定X線がCuKαの場合、且つ半価幅を用いた場合、k=0.94)
λ:測定X線の波長(nm)
β:回折線の半価幅(ラジアン)
θ:回折線のブラッグ角(ラジアン)
The crystallite size of the hexagonal crystal structure of the composite oxide represented by the formula (I) is calculated by the Scherrer formula defined by the following formula (1) using a powder X-ray diffraction method. The measurement peak is near 2θ = 15 °.
D = k × λ / β × cos θ (1)
here,
D: Crystallite diameter (nm)
k: Constant (when the measured X-ray is CuKα and the half width is used, k = 0.94)
λ: wavelength of measured X-ray (nm)
β: Half width of the diffraction line (radians)
θ: Bragg angle of the diffraction line (radians)
 X線回折測定は好ましくは10~70°で行われ、測定対象としては、複合酸化物又は触媒活性成分を担持した複合酸化物を対象とすることができる。X線回折測定は例えば実施例に記載の方法にて行なわれる。 X-ray diffraction measurement is preferably performed at 10 to 70 °, and the target of measurement may be a composite oxide or a composite oxide carrying a catalytically active component. X-ray diffraction measurement is performed, for example, by the method described in the examples.
 式(I)に示す複合酸化物の比表面積は、3m/g以上であることが、触媒活性成分の所望の担持量を得やすい点や高い空間速度条件下でも高い排ガス浄化活性が得られる点で好ましく、20m/g以下であることが、過酷な熱条件下でも急激な表面積の変化が起きづらい点で好ましい。複合酸化物の比表面積は、更に好ましくは5m/g以上15m/g以下である。上述した通り、複合酸化物はその結晶構造の安定性を反映して、比表面積の熱耐久後の維持率も高いものである。複合酸化物の比表面積は950℃以上の熱耐久後であっても上記の範囲内であることが好ましい。複合酸化物の比表面積は、複合酸化物又は触媒活性成分を担持した複合酸化物で測定することができる。熱耐久は例えば空気雰囲気下、950℃、10時間で行うことが好ましい。この条件において、複合酸化物の比表面積の維持率(=熱耐久後の比表面積/熱耐久前の比表面積×100(%))は、65%以上であることが好ましい。比表面積はBET多点法により測定され、具体的には後述の実施例の方法で測定できる。 The specific surface area of the composite oxide represented by the formula (I) is 3 m 2 / g or more, and it is easy to obtain a desired amount of the catalytically active component, and high exhaust gas purification activity can be obtained even under high space velocity conditions. It is preferable at a point, and it is preferable that it is 20 m < 2 > / g or less at the point which is hard to generate | occur | produce a rapid surface area change under severe heat conditions. The specific surface area of the composite oxide is more preferably 5 m 2 / g or more and 15 m 2 / g or less. As described above, the composite oxide reflects the stability of its crystal structure, and also has a high retention rate of the specific surface area after thermal durability. The specific surface area of the composite oxide is preferably within the above range even after heat durability of 950 ° C. or higher. The specific surface area of the composite oxide can be measured with the composite oxide or the composite oxide supporting a catalytically active component. The heat durability is preferably performed, for example, in an air atmosphere at 950 ° C. for 10 hours. Under these conditions, the maintenance ratio of the specific surface area of the composite oxide (= specific surface area after heat endurance / specific surface area before heat endurance × 100 (%)) is preferably 65% or more. The specific surface area is measured by the BET multipoint method, and specifically can be measured by the method of Examples described later.
 式(I)で示される複合酸化物は、例えば共沈法で製造することができる。特許文献1に記載の複合酸化物は、これを共沈法で製造しようとすると、不純物等が生じる傾向にあるので、ソルボサーマル法などの製造工程が複雑な方法で製造する必要がある。これに対し、本発明の複合酸化物は、簡便な共沈法で安定した品質のものが得られるという利点がある。 The composite oxide represented by the formula (I) can be produced, for example, by a coprecipitation method. The complex oxide described in Patent Document 1 tends to generate impurities when it is produced by a coprecipitation method, and therefore, it is necessary to produce the complex oxide by a method having a complicated production process such as a solvothermal method. On the other hand, the complex oxide of the present invention has an advantage that a stable quality can be obtained by a simple coprecipitation method.
 共沈法としては、原料として希土類元素Mの水溶性塩とマンガン化合物とを含む溶液に沈殿剤を添加して、沈殿物を得た後、これを乾燥させ、焼成することにより式(I)で示される複合酸化物を得る方法を挙げることができる。希土類元素Mの水溶性塩としては、硝酸塩やシュウ酸塩、酢酸塩、アンミン錯体塩、塩化物が挙げられる。マンガン化合物としては、マンガンの硝酸塩やシュウ酸塩、酢酸塩、アンミン錯体塩、塩化物が挙げられる。沈殿剤としては、アンモニア水等のアルカリ剤が挙げられる。希土類元素Mの水溶性塩とマンガン化合物とを含む溶液の溶媒としては水が挙げられる。希土類元素Mの水溶性塩とマンガン化合物とを含む溶液におけるマンガンの水溶性塩及びマンガン化合物の濃度(沈殿剤添加前)としては、それぞれ0.01mol/L以上1mol/L以下、特に0.05mol/L以上0.5mol/L以下が好ましい。沈殿剤の好ましい添加量としては、希土類元素M1モルに対して3モル~30モルが好ましく、5モル~15モルがより好ましい。首尾よく目的物を得る点から、焼成温度は、800~1000℃が好ましく、800~950℃がより好ましい。焼成雰囲気は空気が好ましい。 The co-precipitation method, by adding a precipitant to a solution comprising a water soluble salt and a manganese compound of a rare earth element M 1 as the starting material, after obtaining a precipitate, which was dried, expression by calcining (I And a method of obtaining a composite oxide represented by Examples of the water-soluble salts of rare earth elements M 1, nitrates and oxalates, acetates, ammine complex, chloride and the like. Examples of manganese compounds include manganese nitrates, oxalates, acetates, ammine complex salts, and chlorides. Examples of the precipitating agent include alkaline agents such as aqueous ammonia. The solvent for the solution containing a water-soluble salt and manganese compound of a rare earth element M 1 include water. The concentration of the water-soluble salts and manganese compounds manganese in the solution containing a water soluble salt and a manganese compound of a rare earth element M 1 (prior to precipitation additive), respectively 0.01 mol / L or more 1 mol / L or less, particularly 0. 05 mol / L or more and 0.5 mol / L or less are preferable. A preferred addition amount of the precipitating agent is preferably 3 mol to 30 mol, and more preferably 5 mol to 15 mol with respect to 1 mol of the rare earth element M 1 . The firing temperature is preferably 800 to 1000 ° C., more preferably 800 to 950 ° C., from the viewpoint of successfully obtaining the desired product. The firing atmosphere is preferably air.
 式(I)で示される複合酸化物は、特定の製造方法による製造物に限定されるものではなく、ソルボサーマル法及び錯体重合法によっても製造できる。ソルボサーマル法及び錯体重合法の手順としては、特許文献1に記載された方法を応用すればよい。 The composite oxide represented by the formula (I) is not limited to a product produced by a specific production method, and can also be produced by a solvothermal method and a complex polymerization method. As a procedure of the solvothermal method and the complex polymerization method, the method described in Patent Document 1 may be applied.
 式(I)で示される複合酸化物は、触媒活性成分を担持させることができる。式(I)で示される複合酸化物に触媒活性成分を担持させる場合、担持される触媒活性成分は、Pd、Rh、Pt、Ru及びIrから選ばれる少なくとも一種であることが好ましい。触媒活性成分は一種のみであってもよく、二種以上を組みあわせて用いてもよい。触媒活性成分は、複合酸化物中において、メタルの状態であってもよく、酸化物の状態であってもよい。触媒活性成分は、極微量で当該複合酸化物の浄化活性を劇的に向上させる観点から、式(I)で示される複合酸化物に対して、Pd及びRhから選ばれる少なくとも一種であることが好ましく、Pdであることが最も好ましい。 The composite oxide represented by the formula (I) can carry a catalytically active component. When a catalytically active component is supported on the composite oxide represented by the formula (I), the supported catalytically active component is preferably at least one selected from Pd, Rh, Pt, Ru and Ir. Only one type of catalytically active component may be used, or two or more types may be used in combination. The catalytically active component may be in a metal state or an oxide state in the composite oxide. The catalytically active component is at least one selected from Pd and Rh with respect to the composite oxide represented by the formula (I) from the viewpoint of dramatically improving the purification activity of the composite oxide in a very small amount. Preferably, it is Pd.
 触媒活性成分が複合酸化物に担持されているとは、複合酸化物の外表面又は細孔内表面に物理的又は化学的に吸着、結合又は保持されていることをいう。具体的には、複合酸化物が触媒活性成分を担持していることは、例えば走査型電子顕微鏡(SEM)で観察した時の粒径の測定により確認できる。例えば、複合酸化物の表面上に存在している触媒活性成分の平均粒径は当該複合酸化物の平均粒径に対して、10%以下であることが好ましく、3%以下であることがより好ましく、1%以下であることが特に好ましい。ここでいう平均粒径とは、SEMで観察した時の30個以上の複合酸化物や触媒活性成分子の粒径の平均値である。 The phrase “catalytically active component is supported on the composite oxide” means that the composite oxide is physically, chemically adsorbed, bonded or held on the outer surface or the inner surface of the pores. Specifically, it can be confirmed that the composite oxide supports the catalytically active component by measuring the particle diameter when observed with, for example, a scanning electron microscope (SEM). For example, the average particle size of the catalytically active component present on the surface of the composite oxide is preferably 10% or less, more preferably 3% or less with respect to the average particle size of the composite oxide. It is preferably 1% or less. The average particle diameter here is the average value of the particle diameters of 30 or more complex oxides and catalytic active components when observed with an SEM.
 複合酸化物に担持する触媒活性成分の量は、当該複合酸化物100質量%に対し0.01質量%以上であることが、低温での触媒活性が一層得やすい点から好ましい。また、触媒活性成分の量は、式(I)で示される複合酸化物100質量%に対し10質量%以下であることが、コストを低く抑える点で好ましい。これらの観点から、より好ましくは触媒活性成分の量は式(I)で示される複合酸化物100質量%に対し0.01質量%以上5質量%以下であり、更に好ましくは0.05質量%以上2質量%以下である。 The amount of the catalytically active component supported on the composite oxide is preferably 0.01% by mass or more with respect to 100% by mass of the composite oxide from the viewpoint that the catalytic activity at a low temperature is more easily obtained. In addition, the amount of the catalytically active component is preferably 10% by mass or less with respect to 100% by mass of the composite oxide represented by the formula (I) from the viewpoint of keeping costs low. From these viewpoints, the amount of the catalytically active component is more preferably 0.01% by mass or more and 5% by mass or less, more preferably 0.05% by mass with respect to 100% by mass of the composite oxide represented by the formula (I). The content is 2% by mass or less.
 また上記と同様の理由から、排ガス浄化用触媒組成物中の触媒活性成分の量は0.005質量%以上8質量%以下であることが好ましく、0.01質量%以上5質量%以下であることがより好ましく、更に好ましくは0.05質量%以上2質量%以下である。 For the same reason as above, the amount of the catalytically active component in the exhaust gas purification catalyst composition is preferably 0.005% by mass or more and 8% by mass or less, and 0.01% by mass or more and 5% by mass or less. More preferably, it is 0.05 mass% or more and 2 mass% or less.
 複合酸化物に触媒活性成分を担持させるには、触媒活性成分含有溶液に複合酸化物を浸漬させた後、乾燥させ、焼成させることが好ましい。触媒活性成分溶液の調製に用いる貴金属塩としては、例えば、酢酸塩、硝酸塩、アンミン錯体塩、塩化物等を用いることができる。溶媒としては、水やアセトン等を用いることができる。焼成は大気雰囲気下で400℃以上600℃以下、30分以上10時間以下行うことが好ましい。 In order to support the catalytically active component on the composite oxide, it is preferable to immerse the composite oxide in the catalytically active component-containing solution, and then dry and calcinate. As the noble metal salt used for the preparation of the catalytically active component solution, for example, acetate, nitrate, ammine complex salt, chloride and the like can be used. As the solvent, water, acetone or the like can be used. Firing is preferably performed at 400 ° C. to 600 ° C. for 30 minutes to 10 hours in an air atmosphere.
 複合酸化物に対する触媒活性成分の量は、触媒活性成分が担持された複合酸化物材料をアルカリ等で溶解して得られる溶液中のPt、Pd、Rh、Ru、Ir等の貴金属の量並びにMn及び上記希土類元素Mの量をICP発光分光分析法で測定することにより得られる。 The amount of the catalytically active component relative to the composite oxide is determined by the amount of noble metals such as Pt, Pd, Rh, Ru, and Ir in the solution obtained by dissolving the composite oxide material carrying the catalytically active component with an alkali or the like, and Mn. and obtained by measuring the amount of the rare earth element M 1 by ICP emission spectrometry.
 式(I)で示される複合酸化物又は触媒活性成分を担持させてなる当該複合酸化物は、その優れたOSC等の熱的安定性、高温耐久後の排ガス浄化性能を活かして、排ガス浄化触媒として好適に用いることができる。例えば、基材と基材表面に形成される排ガス浄化用触媒層とを有する排ガス浄化用触媒において、排ガス浄化用触媒層に前記複合酸化物、特に好ましくは触媒活性成分を担持した前記複合酸化物を含有させることで、優れた耐熱性及び低温での排ガス浄化性能を有する排ガス浄化用触媒を得ることができる。 The composite oxide obtained by supporting the composite oxide represented by the formula (I) or the catalytically active component is an exhaust gas purification catalyst utilizing its excellent thermal stability such as OSC and the exhaust gas purification performance after high temperature durability. Can be suitably used. For example, in an exhaust gas purification catalyst having a base material and an exhaust gas purification catalyst layer formed on the surface of the base material, the composite oxide, particularly preferably the composite oxide carrying a catalytically active component on the exhaust gas purification catalyst layer By containing, an exhaust gas purification catalyst having excellent heat resistance and exhaust gas purification performance at a low temperature can be obtained.
 上記の基材の形状は、特に限定されるものではないが、一般的にはフロースルー型のハニカム、板、ペレット、又はウォールスルー型のハニカム等の形状であり、好ましくはフロースルー型のハニカム、又はウォールスルー型のハニカムである。また、このような基材の材質としては、例えば、アルミナ(Al)、ムライト(3Al-2SiO)、コージェライト(2MgO-2Al-5SiO)、チタン酸アルミニウム(AlTiO)、炭化ケイ素(SiC)等のセラミックスや、ステンレス等の金属材料を挙げることができる。 The shape of the substrate is not particularly limited, but is generally a shape of a flow-through type honeycomb, a plate, a pellet, or a wall-through type honeycomb, and preferably a flow-through type honeycomb. Or a wall-through type honeycomb. Examples of the material of the base material include alumina (Al 2 O 3 ), mullite (3Al 2 O 3 -2SiO 2 ), cordierite (2MgO-2Al 2 O 3 -5SiO 2 ), and aluminum titanate. Examples thereof include ceramics such as (Al 2 TiO 5 ) and silicon carbide (SiC), and metal materials such as stainless steel.
 排ガス浄化用触媒層を構成する排ガス浄化用触媒組成物は、例えば式(I)で示される複合酸化物又は触媒活性成分を担持した該複合酸化物のみからなるものであってもよいが、それら以外の成分を含有してもよい。
 排ガス浄化用触媒層を構成する排ガス浄化用触媒組成物中の前記複合酸化物以外の成分としては、例えば主に担体としての役割を果すものとして、TiO、SiO、ゼオライト、MgO、MgAlなどの無機多孔質材料、主にOSC材料としての役割を果すものとして、CeO、CeO-ZrO複合酸化物など、NO吸着材としての役割を果たすものとして、Ba、Sr、Mg等のアルカリ土類金属化合物、バインダとしての役割を果たすものとして、アルミナゾルやジルコニアゾル等が挙げられる。
 これらにおいても、上記で例示した触媒活性成分が担持されていることが好ましい。
 排ガス浄化用触媒組成物中、式(I)で示される複合酸化物の量は限定されないが、例えば10質量%以上99.9質量%以下であることが好ましく、20質量%以上98質量%以下であることがより好ましく、40質量%以上95質量%以下であることが特に好ましい。
The exhaust gas-purifying catalyst composition constituting the exhaust gas-purifying catalyst layer may be composed of, for example, the composite oxide represented by the formula (I) or the composite oxide carrying a catalytically active component. You may contain components other than.
Examples of the components other than the composite oxide in the exhaust gas purification catalyst composition constituting the exhaust gas purification catalyst layer include, for example, TiO 2 , SiO 2 , zeolite, MgO, MgAl 2 , mainly serving as a carrier. As an inorganic porous material such as O 4 , mainly serving as an OSC material, such as CeO 2 , CeO 2 —ZrO 2 composite oxide, and the like serving as a NO x adsorbent, Ba, Sr, Examples of the alkaline earth metal compound such as Mg and those serving as a binder include alumina sol and zirconia sol.
Also in these, it is preferable that the catalytically active component exemplified above is supported.
In the exhaust gas purification catalyst composition, the amount of the composite oxide represented by the formula (I) is not limited, but is preferably 10% by mass or more and 99.9% by mass or less, for example, 20% by mass or more and 98% by mass or less. It is more preferable that it is 40 mass% or more and 95 mass% or less.
 式(I)で示される複合酸化物を含めた無機多孔質材料の量は、本発明による耐熱性及び低温での排ガス浄化性能を得る点から、排ガス浄化用触媒組成物中10質量%以上99.9質量%以下であることが好ましく、20質量%以上98質量%以下であることがより好ましく、40質量%以上95質量%以下であることが特に好ましい。 The amount of the inorganic porous material including the composite oxide represented by the formula (I) is 10 mass% or more in the exhaust gas purification catalyst composition from the viewpoint of obtaining heat resistance and low temperature exhaust gas purification performance according to the present invention. It is preferably 9% by mass or less, more preferably 20% by mass or more and 98% by mass or less, and particularly preferably 40% by mass or more and 95% by mass or less.
 式(I)で示される複合酸化物はOSCを有しているところ、式(I)で示される複合酸化物を含めたOSC材料の量は、OSCと、耐熱性及び低温での排ガス浄化性能を発揮させるバランスを考慮して、排ガス浄化用触媒組成物中10質量%以上80質量%以下であることが好ましく、20質量%以上70質量%以下であることがより好ましく、40質量%以上60質量%以下であることが特に好ましい。 Where the composite oxide represented by the formula (I) has OSC, the amount of the OSC material including the composite oxide represented by the formula (I) is OSC, heat resistance, and low temperature exhaust gas purification performance. In consideration of the balance for exhibiting the above, it is preferably 10% by mass or more and 80% by mass or less, more preferably 20% by mass or more and 70% by mass or less, and more preferably 40% by mass or more and 60% by mass or less in the exhaust gas purification catalyst composition. It is particularly preferable that the content is not more than mass%.
 アルカリ土類金属化合物としては、アルカリ土類金属の酸化物や炭酸塩が挙げられ、その量としては、NO吸着性と、耐熱性及び低温での排ガス浄化性能のバランスを考慮して、排ガス浄化用触媒組成物中10質量%以下であることが好ましく、1質量%以上5質量%以下であることがより好ましい。 The alkaline earth metal compounds, include oxides and carbonates of alkaline earth metals, as its amount, taking into consideration the the NO x adsorption properties, the balance of exhaust gas purification performance in heat resistance and low temperature, the exhaust gas It is preferable that it is 10 mass% or less in the catalyst composition for purification, and it is more preferable that it is 1 mass% or more and 5 mass% or less.
 式(I)で示される複合酸化物を含む前記排ガス浄化用触媒組成物を有するスラリーを基材表面に塗布し、乾燥させ、焼成することで、触媒層が基材上に形成された排ガス浄化用触媒を得ることができる。
 例えば触媒活性成分を担持した複合酸化物を有する排ガス浄化用触媒組成物の層を得る場合は、上記式(I)で示される複合酸化物及び、必要に応じてその他の上記成分を、触媒活性成分の水溶性塩を含有する水溶液に投入して排ガス浄化用触媒組成物を含むスラリーを調製し、このスラリーを、基材に塗布し、乾燥、焼成して、排ガス浄化用触媒を形成してもよい。スラリーの固形分含量としては、20質量%以上40質量%以下であることが、排ガス浄化用触媒形成時の作業性の点で好ましい。なお、触媒活性成分を用いずに排ガス浄化用触媒を形成する場合には、上述した触媒活性成分の水溶性塩を含有する水溶液を用いずにスラリーを調製すれば良い。
Exhaust gas purification in which a catalyst layer is formed on a base material by applying a slurry having the exhaust gas purification catalyst composition containing the composite oxide represented by the formula (I) to the surface of the base material, drying, and firing. The catalyst for use can be obtained.
For example, when obtaining a layer of an exhaust gas-purifying catalyst composition having a composite oxide carrying a catalytically active component, the composite oxide represented by the above formula (I) and, if necessary, the other components described above are treated with catalytic activity. A slurry containing an exhaust gas purification catalyst composition is prepared by adding it to an aqueous solution containing a water-soluble salt of the component, and this slurry is applied to a substrate, dried and fired to form an exhaust gas purification catalyst. Also good. The solid content of the slurry is preferably 20% by mass or more and 40% by mass or less from the viewpoint of workability when forming the exhaust gas purifying catalyst. When forming an exhaust gas purifying catalyst without using a catalytically active component, a slurry may be prepared without using an aqueous solution containing the water-soluble salt of the catalytically active component described above.
 また得られる排ガス浄化用触媒の触媒活性の点から、スラリーを塗布した基材を焼成する温度としては、300℃~800℃が好ましく、400℃~600℃がより好ましく、焼成時間としては、0.5時間~10時間が好ましく、1時間~3時間がより好ましい。焼成は大気雰囲気下にて行うことができる。 Further, from the viewpoint of the catalytic activity of the obtained exhaust gas purification catalyst, the temperature for firing the substrate coated with the slurry is preferably 300 ° C. to 800 ° C., more preferably 400 ° C. to 600 ° C., and the firing time is 0 5 hours to 10 hours are preferred, and 1 hour to 3 hours are more preferred. Firing can be performed in an air atmosphere.
 排ガス浄化用触媒において、本発明の排ガス浄化用触媒組成物の量が、60g/L以上であることが本発明による耐熱性及び低温での排ガス浄化性能を得る点から好ましく、160g/L以下であることが背圧の低下を防止しつつ好適な低温活性が得られる点から好ましい。これらの観点から、本発明の排ガス浄化用触媒において、本発明の排ガス浄化用触媒組成物の量は、70g/L以上140g/L以下であることがより好ましく、85g/L以上120g/L以下であることが特に好ましい。ここでいう排ガス浄化用触媒における排ガス浄化用触媒組成物の量は多孔質である基材の孔部の体積を含む基材の体積基準の量である。また、排ガス浄化用触媒における、式(I)で示される複合酸化物の好ましい量としても、上記の排ガス浄化用触媒における本発明の排ガス浄化用触媒組成物の好ましい量と同様の量が挙げられる。 In the exhaust gas purification catalyst, the amount of the exhaust gas purification catalyst composition of the present invention is preferably 60 g / L or more from the viewpoint of obtaining heat resistance and low temperature exhaust gas purification performance according to the present invention, and 160 g / L or less. It is preferable from the point that suitable low-temperature activity can be obtained while preventing a decrease in back pressure. From these viewpoints, in the exhaust gas purification catalyst of the present invention, the amount of the exhaust gas purification catalyst composition of the present invention is more preferably from 70 g / L to 140 g / L, more preferably from 85 g / L to 120 g / L. It is particularly preferred that Here, the amount of the exhaust gas-purifying catalyst composition in the exhaust gas-purifying catalyst is an amount based on the volume of the substrate including the volume of the pores of the porous substrate. Further, the preferable amount of the composite oxide represented by the formula (I) in the exhaust gas purification catalyst may be the same amount as the preferable amount of the exhaust gas purification catalyst composition of the present invention in the exhaust gas purification catalyst. .
 以上の通り、本実施形態の排ガス浄化触媒用材料、排ガス浄化用触媒組成物及び排ガス浄化用触媒は、例えば900℃以上1150℃以下程度の高温に曝されても、安定した排ガス浄化触媒性能、特に低温での排ガス浄化性能を示すことができる。このような排ガス浄化触媒用材料、排ガス浄化用触媒組成物及び排ガス浄化用触媒は、ガソリンエンジンやディーゼルエンジンなど化石燃料を動力源とする内燃機関の排ガス浄化用材料として、安定した高い排ガス浄化性能を発揮することができる。特に本実施形態の排ガス浄化触媒用材料、排ガス浄化用触媒組成物及び排ガス浄化用触媒は、その高い耐熱性から、自動車やバイク等のガソリンエンジンから排出される排ガスを浄化するために用いられることが好ましい。 As described above, the exhaust gas purifying catalyst material, the exhaust gas purifying catalyst composition, and the exhaust gas purifying catalyst of the present embodiment have stable exhaust gas purifying catalyst performance even when exposed to a high temperature of, for example, about 900 ° C. to 1150 ° C. In particular, the exhaust gas purification performance at a low temperature can be shown. Such an exhaust gas purification catalyst material, an exhaust gas purification catalyst composition, and an exhaust gas purification catalyst are stable and high exhaust gas purification performance as an exhaust gas purification material of an internal combustion engine using a fossil fuel as a power source such as a gasoline engine or a diesel engine. Can be demonstrated. In particular, the exhaust gas purifying catalyst material, the exhaust gas purifying catalyst composition, and the exhaust gas purifying catalyst of the present embodiment are used for purifying exhaust gas discharged from gasoline engines such as automobiles and motorcycles because of their high heat resistance. Is preferred.
 以下、実施例により本発明を更に詳細に説明する。しかしながら本発明の範囲は、かかる実施例に制限されない。 Hereinafter, the present invention will be described in more detail with reference to examples. However, the scope of the present invention is not limited to such examples.
 〔実施例1〕
 イッテルビウム化合物として硝酸イッテルビウムn水和物(和光純薬工業社製)を用い、マンガン化合物として硝酸マンガン六水和物(和光純薬工業社製)を用い、沈殿剤として28質量%アンモニア水(和光純薬工業社製)を用いた。硝酸イッテルビウムを0.067mol/L、硝酸マンガンを0.067mol/Lで含む混合水溶液に、上記のアンモニア水を水で3.3質量%に希釈したものを室温(25℃)にて撹拌条件下で添加して共沈物を生成させた。この時のYb、Mn及びアンモニアのモル比は1:1:10であった。添加終了後、室温(25℃)にて1時間程度撹拌し、引き続き1時間静置熟成を行い、共沈物を濾別した。濾別した固形分は400mlの純水で洗浄し、その後、400mlのメタノールで洗浄することで、水とメタノールとを置換した。洗浄後の固形分を室温(25℃)で一晩乾燥させた。その後、破砕し、空気下、800℃で10時間焼成を行い、YbMnO粉末を得た。得られたYbMnO粉末を下記条件のXRFによる組成分析に供したところ、Mnに対するMのモル比(M/Mn)は1.03であった。
[Example 1]
Ytterbium nitrate n-hydrate (manufactured by Wako Pure Chemical Industries, Ltd.) is used as the ytterbium compound, manganese nitrate hexahydrate (manufactured by Wako Pure Chemical Industries, Ltd.) is used as the manganese compound, and 28% by mass ammonia water (Japanese Kogure Pharmaceutical Co., Ltd.) was used. A mixed aqueous solution containing 0.067 mol / L of ytterbium nitrate and 0.067 mol / L of manganese nitrate and a solution obtained by diluting the above aqueous ammonia to 3.3% by mass with water at room temperature (25 ° C.) under stirring conditions To add a coprecipitate. At this time, the molar ratio of Yb, Mn and ammonia was 1: 1: 10. After completion of the addition, the mixture was stirred at room temperature (25 ° C.) for about 1 hour, followed by standing aging for 1 hour, and the coprecipitate was separated by filtration. The solid content separated by filtration was washed with 400 ml of pure water, and then washed with 400 ml of methanol to replace water and methanol. The solid content after washing was dried overnight at room temperature (25 ° C.). Thereafter, it was crushed and fired at 800 ° C. for 10 hours in the air to obtain YbMnO 3 powder. YbMnO 3 powder thus obtained was subjected to composition analysis by XRF under the following conditions, the molar ratio of M 1 for Mn (M 1 / Mn) was 1.03.
  <XRFによる組成分析>
 定量方法としては検量線法を採用した。
 測定機器としてはリガク社製ZSX PrimusIIを用いた。
 測定サンプルの調製は以下のようにした。
 ディスクミル(Retsch製RS200)を用いて、YbMnO粉末を20μm以下(D50)に粉砕した後、粉砕粉1gを加圧成形機にてディスク状に成形し、測定した。
<Composition analysis by XRF>
The calibration curve method was adopted as the quantitative method.
As a measuring instrument, ZSX Primus II manufactured by Rigaku Corporation was used.
The measurement sample was prepared as follows.
The YbMnO 3 powder was pulverized to 20 μm or less (D50) using a disk mill (Retsch RS200), and then 1 g of the pulverized powder was molded into a disk shape with a pressure molding machine and measured.
 〔実施例2〕
 酢酸パラジウムが溶解したアセトン溶液に、実施例1で製造したYbMnO粉末を加えて攪拌してスラリーを得た。アセトン溶液を蒸発乾固後、得られた粉末を空気下で、500℃で30分間焼成して、Pdが担持されたYbMnO粉末を製造した。Pdの量は100質量%のYbMnOに対して、0.1質量%であった。以下、Pdが担持されたYbMnOをPd/YbMnOとも示す。
[Example 2]
To the acetone solution in which palladium acetate was dissolved, the YbMnO 3 powder produced in Example 1 was added and stirred to obtain a slurry. After the acetone solution was evaporated to dryness, the obtained powder was calcined at 500 ° C. for 30 minutes in the air to produce YbMnO 3 powder supporting Pd. The amount of Pd was 0.1% by mass with respect to 100% by mass of YbMnO 3 . Hereinafter also show YbMnO 3 which Pd is supported as Pd / YbMnO 3.
 〔実施例3〕
 酢酸パラジウムのアセトン溶液の添加量を変更して、Pdの量が100質量%のYbMnOに対して1質量%であるPd/YbMnO粉末を製造した。酢酸パラジウムのアセトン溶液の添加量以外の製造条件は、実施例2と同様であった。このPd/YbMnO粉末について製造したままの状態において下記条件のX線回折測定法にて測定したX線回折チャートを図1に示す。図1に示すように、得られたPd/YbMnO粉末はYbMnOの六方晶に由来するピークパターンを有している。得られたX線回折測定結果に基づき上記の算出方法にて六方晶構造の結晶子径を測定したところ、28nmであった。
Example 3
The amount of Pd / YbMnO 3 powder in which the amount of Pd was 1% by mass relative to 100% by mass of YbMnO 3 was manufactured by changing the amount of palladium acetate in acetone. The production conditions other than the addition amount of palladium acetate in acetone were the same as in Example 2. FIG. 1 shows an X-ray diffraction chart measured by the X-ray diffraction measurement method under the following conditions in the as-manufactured state of this Pd / YbMnO 3 powder. As shown in FIG. 1, the obtained Pd / YbMnO 3 powder has a peak pattern derived from a hexagonal crystal of YbMnO 3 . Based on the obtained X-ray diffraction measurement result, the crystallite diameter of the hexagonal crystal structure was measured by the above calculation method, and found to be 28 nm.
  <X線回折測定>
・装置:Ultima IV(リガク社製)
・線源:CuKα線
・管電圧:40kV
・管電流:40mA
・スキャン速度:10°/min
・ステップ:0.02°
・スキャン範囲:2θ=10~70°
<X-ray diffraction measurement>
・ Device: Ultima IV (Rigaku)
-Radiation source: CuKα line-Tube voltage: 40 kV
・ Tube current: 40 mA
・ Scanning speed: 10 ° / min
・ Step: 0.02 °
・ Scanning range: 2θ = 10 ~ 70 °
〔実施例4〕
 酢酸パラジウムのアセトン溶液の添加量を変更してPdの量が100質量%のYbMnOに対して2質量%であるPd/YbMnO粉末を製造した。酢酸パラジウムのアセトン溶液の添加量以外の製造条件は、実施例2と同様であった。
Example 4
Pd / YbMnO 3 powder having a Pd content of 2% by mass with respect to 100% by mass of YbMnO 3 was produced by changing the amount of palladium acetate in acetone. The production conditions other than the addition amount of palladium acetate in acetone were the same as in Example 2.
 〔比較例1〕
 イットリウム化合物として硝酸イットリウムn水和物(和光純薬工業社製)を用い、マンガン化合物として硝酸マンガン六水和物(和光純薬工業社製)を用い、沈殿剤として28質量%アンモニア水(和光純薬工業社製)を用いた。硝酸イットリウムを0.067mol/L、硝酸マンガンを0.067mol/Lで含む混合水溶液に、上記のアンモニア水を水で3.3質量%に希釈したものを室温(25℃)にて撹拌条件下で添加して共沈物を生成させた。この時のY、Mn及びアンモニアのモル比は1:1:10であった。添加終了後、室温(25℃)にて1時間程度撹拌し、1時間静置熟成を行い、共沈物を濾別した。濾別した固形分は400mlの純水により洗浄し、その後、400mlのメタノールで洗浄することで、水をメタノールに置換した。洗浄後の固形分を室温(25℃)で一晩乾燥させた。その後、破砕し、空気下、800℃で10時間焼成を行い、YMnO粉末を得た。
 YbMnOの代わりにYMnO粉末を用いた以外は、実施例3と同様にして、Pdが担持されたYMnO(Pd/YMnO)粉末を得た。
[Comparative Example 1]
Yttrium nitrate n-hydrate (manufactured by Wako Pure Chemical Industries, Ltd.) is used as the yttrium compound, manganese nitrate hexahydrate (manufactured by Wako Pure Chemical Industries, Ltd.) is used as the manganese compound, and 28% by mass ammonia water (Japanese Kogure Pharmaceutical Co., Ltd.) was used. A mixed aqueous solution containing 0.067 mol / L of yttrium nitrate and 0.067 mol / L of manganese nitrate, and the above aqueous ammonia diluted to 3.3% by mass with water are stirred at room temperature (25 ° C.). To add a coprecipitate. At this time, the molar ratio of Y, Mn and ammonia was 1: 1: 10. After completion of the addition, the mixture was stirred at room temperature (25 ° C.) for about 1 hour, left to mature for 1 hour, and the coprecipitate was separated by filtration. The solid content separated by filtration was washed with 400 ml of pure water, and then washed with 400 ml of methanol to replace the water with methanol. The solid content after washing was dried overnight at room temperature (25 ° C.). Thereafter, the mixture was crushed and fired at 800 ° C. for 10 hours in the air to obtain YMnO 3 powder.
Except for using the YMnO 3 powder instead of YbMnO 3, the same procedure as in Example 3, Pd was obtained YMnO 3 (Pd / YMnO 3) powder carried.
 〔比較例2〕
 硝酸マンガン六水和物の代わりに鉄化合物として硝酸鉄九水和物(和光純薬工業社製)の水溶液を用いた以外は実施例3と同様にして、Pdが担持されたYbFeO(Pd/YbFeO)粉末を得た。このPd/YbFeO粉末について、実施例3と同様、製造したままの状態でX線回折測定した結果を図1に併せて示す。図1の通り、YbFeOは斜方晶の結晶構造を有していた。
[Comparative Example 2]
In the same manner as in Example 3 except that an aqueous solution of iron nitrate nonahydrate (manufactured by Wako Pure Chemical Industries, Ltd.) was used as the iron compound instead of manganese nitrate hexahydrate, YbFeO 3 (Pd / YbFeO 3 ) powder was obtained. This Pd / YbFeO 3 powder, as in Example 3, are also shown the results of X-ray diffraction measurement in a state prepared to FIG. As shown in FIG. 1, YbFeO 3 had an orthorhombic crystal structure.
 〔比較例3〕
 酢酸イッテルビウム四水和物(Yb(OAc)・4HO,15mmol)、トリスアセチルアセトナト鉄(III)(Fe(acac),9mmol)およびトリスアセチルアセトナトマンガン(III)(Mn(acac),6mmol)を乳鉢で磨砕したのち、プラスチック容器内で超音波を用いて1,4-ブタンジオール(1,4-BG)120ml中に懸濁させた。なお、Fe(acac)とMn(acac)の仕込み量は合計で15mmolとした(Fe9mmol, Mn6mmol)。この懸濁液をオートクレーブ反応管に移し、オートクレーブ(300mL)に仕込み、間隙にも30mlの1,4-BGを加えた。オートクレーブ内を窒素置換したのち、室温から2.3℃/minで315℃まで昇温し、2時間反応させた。生成物をメタノールで洗浄し乾燥させた。その後、破砕し、空気雰囲気下,500℃で30分間焼成を行ない、YbFe0.6Mn0.4粉末を得た。
 次いで、実施例3と同様にしてYbFe0.6Mn0.4にPdを担持させ、Pdの量が100質量%のYbFe0.6Mn0.4に対して1質量%であるPd/YbFe0.6Mn0.4粉末を製造した。
[Comparative Example 3]
Ytterbium acetate tetrahydrate (Yb (OAc) 3 .4H 2 O, 15 mmol), trisacetylacetonatoiron (III) (Fe (acac) 3 , 9 mmol) and trisacetylacetonatomanganese (III) (Mn (acac 3 , 6 mmol) was ground in a mortar and then suspended in 120 ml of 1,4-butanediol (1,4-BG) using a ultrasonic wave in a plastic container. The total charge of Fe (acac) 3 and Mn (acac) 3 was 15 mmol (Fe 9 mmol, Mn 6 mmol). This suspension was transferred to an autoclave reaction tube, charged into an autoclave (300 mL), and 30 ml of 1,4-BG was also added to the gap. After the inside of the autoclave was purged with nitrogen, the temperature was raised from room temperature to 315 ° C. at 2.3 ° C./min and reacted for 2 hours. The product was washed with methanol and dried. Thereafter, it was crushed and fired at 500 ° C. for 30 minutes in an air atmosphere to obtain YbFe 0.6 Mn 0.4 O 3 powder.
Next, Pd was supported on YbFe 0.6 Mn 0.4 O 3 in the same manner as in Example 3, and the amount of Pd was 1% by mass with respect to 100% by mass of YbFe 0.6 Mn 0.4 O 3 . A Pd / YbFe 0.6 Mn 0.4 O 3 powder was produced.
 このPd/YbFe0.6Mn0.4について実施例3と同様、製造したままの状態でX線回折測定した結果を図1に併せて示す。Pd/YbFe0.6Mn0.4におけるYbFe0.6Mn0.4は実施例3と同様の六方晶構造を有していたが、その結晶性は低かった。得られたX線回折測定結果に基づき上記の算出方法にて六方晶構造の結晶子径を測定したところ、22nmであった。 The result of X-ray diffraction measurement of this Pd / YbFe 0.6 Mn 0.4 O 3 in the same state as produced in Example 3 is also shown in FIG. YbFe 0.6 Mn 0.4 O 3 in Pd / YbFe 0.6 Mn 0.4 O 3 had a similar hexagonal structure as in Example 3, but its crystallinity was low. Based on the obtained X-ray diffraction measurement result, the crystallite diameter of the hexagonal crystal structure was measured by the above calculation method, and found to be 22 nm.
 〔比較例4〕
 YbMnOに代えて触媒学会提供の参照触媒であるγ―Al(JRC―ALO―7)を用いた以外は、実施例3と同様にして、Pdが担持されたアルミナ(Pd/Al)粉末を得た。
[Comparative Example 4]
Pd-supported alumina (Pd / Al) in the same manner as in Example 3 except that γ-Al 2 O 3 (JRC-ALO-7), which is a reference catalyst provided by the Catalysis Society of Japan, was used instead of YbMnO 3. 2 O 3 ) powder was obtained.
 〔比較例5〕
 CeOの含有割合が40質量%であるCeO-ZrO固溶体材料(CeO-ZrO材料)を用意した。
 1質量%濃度の硝酸パラジウム水溶液に、CeO-ZrO材料を加えて攪拌してスラリーを得た。このスラリーを空気下で500℃2時間で焼成して、Pd/CeO-ZrO材料粉末を製造した。Pdの量は100質量%のCeO-ZrOに対して、1質量%であった。
[Comparative Example 5]
A CeO 2 —ZrO 2 solid solution material (CeO 2 —ZrO 2 material) having a CeO 2 content of 40% by mass was prepared.
A CeO 2 —ZrO 2 material was added to a 1% by mass palladium nitrate aqueous solution and stirred to obtain a slurry. This slurry was fired under air at 500 ° C. for 2 hours to produce a Pd / CeO 2 —ZrO 2 material powder. The amount of Pd was 1% by mass with respect to 100% by mass of CeO 2 —ZrO 2 .
 実施例及び比較例で得られた粉末について以下の評価に供した。以下の評価では、実施例及び比較例で得られた粉末を排ガス浄化用触媒組成物とも呼ぶ。 The powder obtained in Examples and Comparative Examples was subjected to the following evaluation. In the following evaluation, the powders obtained in Examples and Comparative Examples are also referred to as exhaust gas purification catalyst compositions.
  <耐久試験条件1>
 実施例3及び比較例1で作製した排ガス浄化用触媒組成物について、空気雰囲気下、950℃、30分の耐久焼成を行った。
<Endurance test condition 1>
The exhaust gas-purifying catalyst composition produced in Example 3 and Comparative Example 1 was subjected to durable firing at 950 ° C. for 30 minutes in an air atmosphere.
<評価1:耐久試験1の前後のNO、HC、CO浄化性能>
 耐久試験条件1の焼成前後における実施例3及び比較例1の排ガス浄化用触媒組成物について、常圧固定床流通型反応装置を用いてNO、HC、CO浄化性能を評価した。反応装置内に耐久後の排ガス浄化用触媒組成物200mgを設置し、前処理ガスとして500℃のヘリウムをSV=0.12gsmL-1となる流量で流通させた。次いで、A/F=14.7となる下記の組成の模擬排ガスを、触媒組成物を100℃から500℃まで10℃/minで昇温させるようにSV=0.12gsmL-1となる流量で流通させて、出口ガス成分における各成分量を測定した。NOがNに転化される際の転化率が50%に達したときの装置入口のガス温度、及びCO及びCがCOに転化される際の転化率が50%に達したときの装置入口のガス温度をそれぞれライトオフ温度T50として調べた。C・CO・CO・N濃度の測定は島津製作所社製GC-8AITを用いて行った。結果を表1に示す。
模擬排ガス(組成は体積比率である):C:250ppm、CO:1000ppm、CO2:0%、O2:1125ppm、NO:1000ppm、H2O:0%、及びHeバランス
 また、耐久試験条件1の焼成前のT50(製造条件における「500℃・30分」より「T50500℃・30分」ともいう)と、耐久試験条件1の焼成後である950℃・30分のT50950℃・30分に基づき算出されるT50維持率=(T50500℃・30分/T50950℃・30分)×100(%)を求めた。
<Evaluation 1: NO x , HC, CO purification performance before and after endurance test 1>
The exhaust gas purification catalyst compositions of Example 3 and Comparative Example 1 before and after firing under durability test condition 1 were evaluated for NO x , HC and CO purification performance using an atmospheric pressure fixed bed flow type reactor. 200 mg of the exhaust gas purification catalyst composition after durability was placed in the reactor, and helium at 500 ° C. was circulated as a pretreatment gas at a flow rate of SV = 0.12 gsmL −1 . Next, a simulated exhaust gas having the following composition with A / F = 14.7 is set at a flow rate of SV = 0.12 gsmL −1 so that the catalyst composition is heated from 100 ° C. to 500 ° C. at a rate of 10 ° C./min. The amount of each component in the outlet gas component was measured. The gas temperature at the inlet of the apparatus when the conversion rate when NO x is converted to N 2 reaches 50%, and the conversion rate when CO and C 3 H 6 are converted to CO 2 reach 50% The gas temperature at the inlet of the apparatus was examined as the light-off temperature T50. The C 3 H 6 , CO, CO 2 and N 2 concentrations were measured using GC-8AIT manufactured by Shimadzu Corporation. The results are shown in Table 1.
Simulated exhaust gas (composition is volume ratio): C 3 H 6 : 250 ppm, CO: 1000 ppm, CO 2 : 0%, O 2 : 1125 ppm, NO: 1000 ppm, H 2 O: 0%, and He balance T50 before firing under test condition 1 (also referred to as “T50 500 ° C · 30 minutes” from “500 ° C. · 30 minutes” in manufacturing conditions) and T50 950 after firing at endurance test condition 1 at 950 ° C. for 30 minutes. T50 maintenance rate calculated on the basis of ° C · 30 minutes = (T50 500 ° C · 30 minutes / T50 950 ° C · 30 minutes ) × 100 (%) was determined.
Figure JPOXMLDOC01-appb-T000001
Figure JPOXMLDOC01-appb-T000001
 表1に記載の通り、実施例3の排ガス浄化用触媒組成物は、担体としてYMnO粉末を用いた比較例1に比べて、ガソリン車用の排ガス浄化用触媒において求められる一般的な耐久温度である950℃での耐久後においても、低温でのNO、HC、CO浄化性能に優れていることが判る。
 また、実施例3の排ガス浄化用触媒組成物は、比較例1に比べて、耐久による劣化がほとんど進行せず、耐久後の排ガス浄化性能が非常に高いことが判る。
As shown in Table 1, the exhaust gas purification catalyst composition of Example 3 has a general durability temperature required for an exhaust gas purification catalyst for gasoline vehicles, as compared with Comparative Example 1 using YMnO 3 powder as a carrier. It can be seen that even after endurance at 950 ° C., the NO x , HC, and CO purification performance at low temperatures is excellent.
Further, it can be seen that the exhaust gas purification catalyst composition of Example 3 hardly deteriorates due to durability compared with Comparative Example 1, and the exhaust gas purification performance after durability is very high.
  <耐久試験条件2>
 実施例2~4及び比較例2~4で作製した排ガス浄化用触媒組成物について、空気雰囲気下、950℃、10時間の耐久焼成を行った。
<Endurance test condition 2>
The exhaust gas purifying catalyst compositions prepared in Examples 2 to 4 and Comparative Examples 2 to 4 were subjected to durable firing at 950 ° C. for 10 hours in an air atmosphere.
<評価2:耐久試験2の前後のNO、HC、CO浄化性能>
 耐久試験条件2の焼成前後における実施例2~4及び比較例2~4の排ガス浄化用触媒組成物について、常圧固定床流通型反応装置を用いてNO、HC、CO浄化性能を評価した。焼成前後のT50の評価方法は、評価1と同様である。
 耐久試験条件2の焼成前のT50(T50500℃・30分)と、焼成後である950℃・10時間のT50950℃・10時間に基づき算出されるT50維持率=(T50500℃・30分/T50950℃・10時間)×100(%)を求めた。
<Evaluation 2: NO x , HC, CO purification performance before and after endurance test 2>
Regarding the exhaust gas purifying catalyst compositions of Examples 2 to 4 and Comparative Examples 2 to 4 before and after firing under the durability test condition 2, NO x , HC and CO purification performance was evaluated using an atmospheric pressure fixed bed flow type reactor. . The evaluation method of T50 before and after firing is the same as in Evaluation 1.
T50 maintenance ratio calculated based on T50 (T50 500 ° C./30 minutes ) before firing in durability test condition 2 and T50 950 ° C. · 10 hours after firing 950 ° C. · 10 hours = (T50 500 ° C. · 30 Min / T50 950 ° C., 10 hours ) × 100 (%).
Figure JPOXMLDOC01-appb-T000002
Figure JPOXMLDOC01-appb-T000002
 表2に記載の通り、実施例2~4の排ガス浄化用触媒組成物は、担体としてYbFeO粉末、YbFe0.6Mn0.4粉末、アルミナ粉末をそれぞれ用いた比較例2~4に比べて、ガソリン車用の排ガス浄化用触媒において求められる一般的な耐久温度である950℃での耐久後においても、低温でのNO、HC、CO浄化性能に優れていることが判る。
 また、実施例2~4の排ガス浄化用触媒組成物は、比較例2~4に比べて、耐久による劣化がほとんど進行せず、耐久後の排ガス浄化性能が非常に高いことが判る。
As shown in Table 2, the exhaust gas purifying catalyst compositions of Examples 2 to 4 were compared with Comparative Examples 2 to 4 using YbFeO 3 powder, YbFe 0.6 Mn 0.4 O 3 powder, and alumina powder, respectively, as carriers. It can be seen that even after endurance at 950 ° C., which is a general endurance temperature required for exhaust gas purification catalysts for gasoline vehicles, it is excellent in NO x , HC and CO purification performance at low temperatures.
In addition, it can be seen that the exhaust gas purification catalyst compositions of Examples 2 to 4 hardly deteriorate due to durability compared to Comparative Examples 2 to 4, and the exhaust gas purification performance after durability is very high.
 <評価3:耐久後のOSC量>
 実施例2、3及び比較例5で得られた排ガス浄化用触媒組成物を、下記雰囲気下、900℃、25時間の耐久焼成に供した。
 耐久試験雰囲気(組成は体積基準):A/F=14.6,CO:0.50%, H2:0.17%, O2:0.50% NO(NOx):500ppm, C3H6(HC):1200ppmC, CO2:14%, H2O:10%, N2:balance
 耐久焼成後の排ガス浄化用触媒組成物のOSCの測定をCOパルス法で行った。OSC測定では、排ガス浄化用触媒組成物を石英製反応容器に入れ、He流通下800℃に昇温して当該温度を10分間保持した。そして、800℃を保持した状態でOガスを5パルスに分けて注入し酸化処理をした後、COを含有する試験用ガスを20パルスに分けて注入し、消費されたCOガス総量から800℃における組成物粉末単位質量当たりの総OSC量(μmol/g)をULVAC製、RG702により測定した。なお、前記試験用ガスはHeガス75容量%にCOガスを25容量%希釈させて調製した。結果を表3に示す。
<Evaluation 3: OSC amount after endurance>
The exhaust gas-purifying catalyst compositions obtained in Examples 2 and 3 and Comparative Example 5 were subjected to durable firing at 900 ° C. for 25 hours under the following atmosphere.
Durability test atmosphere (composition volume basis): A / F = 14.6, CO: 0.50%, H 2: 0.17%, O 2: 0.50% NO (NO x): 500ppm, C 3 H 6 (HC): 1200ppmC, CO 2 : 14%, H 2 O: 10%, N 2 : balance
The OSC of the exhaust gas purification catalyst composition after the durable firing was measured by the CO pulse method. In the OSC measurement, the exhaust gas-purifying catalyst composition was put in a quartz reaction vessel, heated to 800 ° C. under He flow, and maintained at that temperature for 10 minutes. Then, after maintaining the temperature of 800 ° C. and injecting O 2 gas into 5 pulses and performing oxidation treatment, a test gas containing CO is injected in 20 pulses, and the total amount of consumed CO gas is 800 The total amount of OSC (μmol / g) per unit mass of the composition powder at ° C. was measured by ULVAC, RG702. The test gas was prepared by diluting 25% by volume of CO gas into 75% by volume of He gas. The results are shown in Table 3.
Figure JPOXMLDOC01-appb-T000003
Figure JPOXMLDOC01-appb-T000003
 表3の通り、YbMnO粉末を用いた実施例3の排ガス浄化用触媒組成物は、比較例5である一般的な排ガス浄化用触媒組成物に対しても、高温耐久後のOSC能が高く、耐熱性が高いことが判る。また、実施例3に対してPd担持量が1/10である実施例2であっても、高温耐久後のOSC能が高く、耐熱性が高いことが判る。 As shown in Table 3, the exhaust gas purification catalyst composition of Example 3 using YbMnO 3 powder has a higher OSC ability after high temperature durability than the general exhaust gas purification catalyst composition of Comparative Example 5. It can be seen that the heat resistance is high. Further, even in Example 2 in which the amount of Pd supported is 1/10 of Example 3, it can be seen that the OSC ability after high-temperature durability is high and the heat resistance is high.
 <評価4:触媒活性成分量の影響>
 上記耐久試験条件2の焼成後の実施例1、実施例2、比較例4の排ガス浄化用触媒組成物について、上記評価1と同様の方法にて100℃から500℃まで10℃/minで昇温させるように模擬排ガスをSV=0.12gsmL-1となる流量で流通させたときの、装置入口の各ガス温度における、NOがNに転化される際の転化率、及びCO及びCがCOに転化される際の転化率を調べた。得られたグラフを図2に示す。
<Evaluation 4: Influence of amount of catalytically active component>
The exhaust gas purification catalyst compositions of Example 1, Example 2 and Comparative Example 4 after firing under the above durability test condition 2 were increased from 100 ° C. to 500 ° C. at 10 ° C./min in the same manner as in the above evaluation 1. When the simulated exhaust gas is circulated at a flow rate of SV = 0.12 gsmL −1 so as to be heated, the conversion rate when NO x is converted to N 2 at each gas temperature at the apparatus inlet, and CO and C The conversion rate when 3 H 6 was converted to CO 2 was examined. The obtained graph is shown in FIG.
 図2に示すように実施例1の排ガス浄化用触媒組成物は触媒活性成分を非含有であっても排ガス浄化触媒活性を有していること、実施例2のように触媒活性成分量が0.1質量%と微量であっても、比較例4のアルミナに触媒活性成分を1質量%担持した組成物よりも優れた排ガス浄化触媒活性を示すことが判る。従って、本発明の複合酸化物を用いることにより、使用する貴金属量の低減と排ガス浄化触媒性能の向上を両立させることが可能である。 As shown in FIG. 2, the exhaust gas purifying catalyst composition of Example 1 has an exhaust gas purifying catalytic activity even when it does not contain a catalytic active component, and the amount of catalytic active component is 0 as in Example 2. It can be seen that even when the amount is as small as 1% by mass, the catalyst of the exhaust gas purification catalyst activity is superior to that of the composition of Comparative Example 4 in which 1% by mass of the catalytically active component is supported. Therefore, by using the composite oxide of the present invention, it is possible to achieve both reduction in the amount of noble metal used and improvement in exhaust gas purification catalyst performance.
<評価5:結晶構造の耐熱性>
 実施例3、比較例3、比較例4の排ガス浄化用触媒組成物について、上記<耐久試験条件2>の耐久試験(以下単に耐久試験2ともいう)の前後において測定したX線回折チャートを図3に示す。X線回折測定法は上記条件を採用した。各排ガス浄化用触媒組成物について、耐久試験2の前後の比表面積並びに比表面積の維持率(=耐久後比表面積/耐久前比表面積×100(%))を表4に示す。
 <比表面積の測定方法>
 比表面積の測定は、マイクロトラックベル社製BEL SORP-mini II-HSPを用いてBET多点法(測定ガス:窒素)にて行った。
<Evaluation 5: Heat resistance of crystal structure>
The X-ray diffraction charts measured for the exhaust gas purifying catalyst compositions of Example 3, Comparative Example 3, and Comparative Example 4 before and after the durability test of <Durability Test Condition 2> (hereinafter also simply referred to as Durability Test 2) are shown in the figure. 3 shows. The above conditions were adopted for the X-ray diffraction measurement method. Table 4 shows the specific surface area before and after the durability test 2 and the maintenance ratio of the specific surface area (= specific surface area after durability / specific surface area before durability × 100 (%)) for each exhaust gas purifying catalyst composition.
<Method for measuring specific surface area>
The specific surface area was measured by BET multipoint method (measurement gas: nitrogen) using BEL SORP-mini II-HSP manufactured by Microtrack Bell.
Figure JPOXMLDOC01-appb-T000004
Figure JPOXMLDOC01-appb-T000004
 図3の通り、実施例3のPd/YbMnO粉末は耐久試験2前後のいずれにおいても、YbMnOの六方晶に由来するピークパターンを有しており、<耐久試験条件2>の耐久試験前後において、そのピークパターンにほぼ変化はなく、耐久後も製造時の結晶構造が保たれている。これに対し、比較例3のPd/YbFe0.6Mn0.4は、耐久試験2の後にピークが非常に鋭くなり、結晶構造が大きく変化している。このことを裏付けるように表4の通り、実施例3の比表面積の耐久後の維持率は69.2%と高いのに対し、比較例3では、比表面積の耐久後の維持率は、12.8%と大幅に劣っている。
 また、一般的に耐熱性が高いといわれるAlにPdを担持させた比較例4のPd/Alは、耐久試験2の前後でピークパターンの変化が少なく、比表面積の耐久後の維持率も一定程度高いものの、実施例3のPd/YbMnOの比表面積の耐久前後の維持率は表4の通り、それを上回ることも判る。
As shown in FIG. 3, the Pd / YbMnO 3 powder of Example 3 had a peak pattern derived from the hexagonal YbMnO 3 before and after the endurance test 2, and before and after the endurance test of <endurance test condition 2>. However, there is almost no change in the peak pattern, and the crystal structure at the time of manufacture is maintained after the endurance. On the other hand, Pd / YbFe 0.6 Mn 0.4 O 3 of Comparative Example 3 has a very sharp peak after the durability test 2 and the crystal structure is greatly changed. To confirm this, as shown in Table 4, the retention rate after endurance of the specific surface area of Example 3 was as high as 69.2%, whereas in Comparative Example 3, the retention rate after endurance of the specific surface area was 12%. It is significantly inferior at 8%.
In addition, Pd / Al 2 O 3 of Comparative Example 4 in which Pd is supported on Al 2 O 3 , which is generally said to have high heat resistance, has little change in peak pattern before and after durability test 2 and has a specific surface area durability. Although the subsequent maintenance rate is also high to some extent, it can also be seen that the maintenance rate before and after the endurance of the specific surface area of Pd / YbMnO 3 of Example 3 exceeds that as shown in Table 4.
 なお、図1及び3より、実施例3の六方晶に由来するピークパターンと、比較例3の六方晶に由来するピークパターンは、異なることが判る。例えば、実施例3のピークパターンでは、2θ=28°以上32°以下の範囲において、29°~30°と30°~31°と31°~32°の位置に3つのピークが観察されるのに対して、比較例3のピークパターンでは、28°~30°と30°~32°の位置に2つのピークしか観察されない。このように、実施例3と比較例3の結晶構造は、同じ六方晶といえども、詳細に見ると異なっている。このような結晶構造の違いも、実施例3の排ガス浄化用触媒組成物が、比較例3に比べて、耐久後の排ガス浄化性能が高くなる要因の1つであると考えることもできる。 1 and 3, it can be seen that the peak pattern derived from the hexagonal crystal of Example 3 and the peak pattern derived from the hexagonal crystal of Comparative Example 3 are different. For example, in the peak pattern of Example 3, three peaks are observed at positions of 29 ° to 30 °, 30 ° to 31 °, and 31 ° to 32 ° in the range of 2θ = 28 ° to 32 °. On the other hand, in the peak pattern of Comparative Example 3, only two peaks are observed at positions of 28 ° to 30 ° and 30 ° to 32 °. Thus, the crystal structures of Example 3 and Comparative Example 3 are different in detail even though they are the same hexagonal crystal. Such a difference in crystal structure can also be considered to be one of the factors in which the exhaust gas purification catalyst composition of Example 3 has higher exhaust gas purification performance after endurance than Comparative Example 3.
 本発明によれば、高温耐久後の排ガス浄化性能が高く、耐熱性に優れた排ガス浄化触媒用材料及び排ガス浄化用触媒組成物並びに排ガス浄化用触媒が提供される。 According to the present invention, there are provided an exhaust gas purification catalyst material, an exhaust gas purification catalyst composition, and an exhaust gas purification catalyst that have high exhaust gas purification performance after endurance at high temperatures and are excellent in heat resistance.

Claims (10)

  1.  式(I)で示される複合酸化物からなる排ガス浄化触媒用材料。
     MMnO・・・(I)
    (式中、MはGd、Tb、Dy、Ho、Er、Tm、Yb及びLuから選ばれる少なくとも一種の希土類元素を示す。)
    A material for exhaust gas purification catalyst comprising a composite oxide represented by the formula (I).
    M 1 MnO 3 (I)
    (In the formula, M 1 represents at least one rare earth element selected from Gd, Tb, Dy, Ho, Er, Tm, Yb, and Lu.)
  2.  前記式(I)におけるMが、Er、Tm、Yb及びLuから選ばれる少なくとも1種の希土類元素である、請求項1に記載の排ガス浄化触媒用材料。 The exhaust gas purifying catalyst material according to claim 1, wherein M 1 in the formula (I) is at least one rare earth element selected from Er, Tm, Yb and Lu.
  3.  前記式(I)で示される複合酸化物の結晶構造が、六方晶構造である、請求項1又は2に記載の排ガス浄化触媒用材料。 The exhaust gas purifying catalyst material according to claim 1 or 2, wherein a crystal structure of the composite oxide represented by the formula (I) is a hexagonal crystal structure.
  4.  前記式(I)で示される複合酸化物の六方晶構造の結晶子径が、25nm以上100nm以下である、請求項3に記載の排ガス浄化触媒用材料。 The exhaust gas purification catalyst material according to claim 3, wherein a crystallite diameter of a hexagonal structure of the composite oxide represented by the formula (I) is 25 nm or more and 100 nm or less.
  5.  請求項1~4の何れか1項に記載の排ガス浄化触媒用材料と触媒活性成分とを含有する排ガス浄化用触媒組成物。 An exhaust gas purifying catalyst composition comprising the exhaust gas purifying catalyst material according to any one of claims 1 to 4 and a catalytically active component.
  6.  前記式(I)で示される複合酸化物に対し、前記触媒活性成分の量が0.01質量%以上10質量%以下である、請求項5に記載の排ガス浄化用触媒組成物。 The catalyst composition for exhaust gas purification according to claim 5, wherein the amount of the catalytically active component is 0.01% by mass or more and 10% by mass or less with respect to the composite oxide represented by the formula (I).
  7.  前記触媒活性成分としてPdを含有する、請求項5又は6に記載の排ガス浄化用触媒組成物。 The exhaust gas purifying catalyst composition according to claim 5 or 6, which contains Pd as the catalytic active component.
  8.  請求項1~4の何れか1項に記載の排ガス浄化触媒用材料を含有し、触媒活性成分を含有しない排ガス浄化用触媒組成物。 An exhaust gas purifying catalyst composition containing the exhaust gas purifying catalyst material according to any one of claims 1 to 4 and containing no catalytically active component.
  9.  基材と、
     前記基材の表面に形成された、請求項5~8の何れか1項に記載の排ガス浄化用触媒組成物の層と、を有する排ガス浄化触媒。
    A substrate;
    An exhaust gas purification catalyst comprising a layer of the exhaust gas purification catalyst composition according to any one of claims 5 to 8, formed on a surface of the base material.
  10.  前記排ガス浄化用触媒組成物を基材に対して60g/L以上160g/L以下の量で有する請求項9に記載の排ガス浄化触媒。 The exhaust gas purification catalyst according to claim 9, wherein the exhaust gas purification catalyst composition is contained in an amount of 60 g / L or more and 160 g / L or less with respect to the base material.
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Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN114308018A (en) * 2021-12-10 2022-04-12 瑞燃(上海)环境工程技术有限公司 Manganese complex valence state cross-linked substance adsorption catalysis material and preparation method and application thereof

Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH0986928A (en) * 1994-10-04 1997-03-31 Nissan Motor Co Ltd A-site deficient perovskite double oxide and catalyst composed thereof
JP2007216099A (en) * 2006-02-14 2007-08-30 Honda Motor Co Ltd Exhaust gas purification oxidation catalyst
JP2011189306A (en) * 2010-03-16 2011-09-29 Honda Motor Co Ltd Catalyst for cleaning exhaust gas
JP2015136684A (en) * 2014-01-24 2015-07-30 三菱重工業株式会社 Exhaust gas treatment catalyst, exhaust gas treatment system and method using the catalyst

Patent Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH0986928A (en) * 1994-10-04 1997-03-31 Nissan Motor Co Ltd A-site deficient perovskite double oxide and catalyst composed thereof
JP2007216099A (en) * 2006-02-14 2007-08-30 Honda Motor Co Ltd Exhaust gas purification oxidation catalyst
JP2011189306A (en) * 2010-03-16 2011-09-29 Honda Motor Co Ltd Catalyst for cleaning exhaust gas
JP2015136684A (en) * 2014-01-24 2015-07-30 三菱重工業株式会社 Exhaust gas treatment catalyst, exhaust gas treatment system and method using the catalyst

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN114308018A (en) * 2021-12-10 2022-04-12 瑞燃(上海)环境工程技术有限公司 Manganese complex valence state cross-linked substance adsorption catalysis material and preparation method and application thereof
CN114308018B (en) * 2021-12-10 2023-07-28 瑞燃(上海)环境工程技术有限公司 Manganese composite valence state crosslinking substance adsorption catalytic material and preparation method and application thereof

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