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WO2021059777A1 - Organic matter decomposition catalyst, and organic matter decomposition device - Google Patents

Organic matter decomposition catalyst, and organic matter decomposition device Download PDF

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Publication number
WO2021059777A1
WO2021059777A1 PCT/JP2020/030343 JP2020030343W WO2021059777A1 WO 2021059777 A1 WO2021059777 A1 WO 2021059777A1 JP 2020030343 W JP2020030343 W JP 2020030343W WO 2021059777 A1 WO2021059777 A1 WO 2021059777A1
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catalyst
organic matter
platinum
decomposition
gas
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PCT/JP2020/030343
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French (fr)
Japanese (ja)
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出村隆充
佐藤秀人
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株式会社村田製作所
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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
    • B01D53/74General processes for purification of waste gases; Apparatus or devices specially adapted therefor
    • B01D53/86Catalytic processes
    • 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
    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02PCLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
    • Y02P20/00Technologies relating to chemical industry
    • Y02P20/50Improvements relating to the production of bulk chemicals
    • Y02P20/52Improvements relating to the production of bulk chemicals using catalysts, e.g. selective catalysts

Definitions

  • the present invention relates to an organic matter decomposition catalyst used for decomposing an organic substance and an organic matter decomposition apparatus provided with an organic matter decomposition catalyst.
  • catalysts for decomposing organic substances used for decomposing organic substances are known.
  • Patent Document 1 describes a catalyst in which a metal catalyst made of a metal or a metal oxide is supported on a carrier made of aluminum nitride. Patent Document 1 describes that this catalyst has high mechanical strength and high thermal conductivity.
  • the catalyst described in Patent Document 1 is produced by the following method. First, the aluminum nitride powder is calcined at 900 ° C. to 1000 ° C. in the presence of air or oxygen to form an aluminum oxide layer on the surface of the aluminum nitride particles. Subsequently, the aqueous solution containing the copper metal particles is impregnated with the aluminum nitride particles and then dried to obtain a catalyst in which the copper fine particles are supported on the surface of the aluminum nitride. Then, the obtained catalyst is calcined in a temperature range of 350 ° C. to 600 ° C. to obtain catalyst particles.
  • an aluminum oxide layer is formed on the surface of the aluminum nitride particles, but the aluminum oxide layer has a lower thermal conductivity than the aluminum nitride, so that the thermal conductivity of the carrier is low. The rate drops. Therefore, when the catalyst is used in a high temperature environment, heat dissipation does not proceed sufficiently, and sintering of the supported metal fine particles easily proceeds, which may reduce the activity of the catalyst.
  • the present invention solves the above-mentioned problems, and an organic substance decomposition catalyst capable of suppressing a decrease in catalytic activity when used in a high temperature environment, and an organic substance provided with such an organic substance decomposition catalyst. It is an object of the present invention to provide a disassembling device.
  • the catalyst for decomposing an organic substance of the present invention is a catalyst for decomposing an organic substance used for decomposing an organic substance, and comprises a carrier and platinum supported on the carrier, and the carrier is present on the surface of N. It is characterized by containing aluminum nitride having an atomic% ratio N / Al of 0.40 or more and 0.50 or less.
  • the catalyst for decomposing organic substances of the present invention it is possible to suppress a decrease in catalytic activity when used in a high temperature environment.
  • the catalyst for decomposing an organic substance according to the present invention is a catalyst for decomposing an organic substance used for decomposing an organic substance, and comprises a carrier and platinum supported on the carrier, and the carrier is composed of N and Al existing on the surface thereof. It satisfies the requirement of containing aluminum nitride having an atomic% ratio N / Al of 0.40 or more and 0.50 or less (hereinafter, referred to as the requirement of the present invention).
  • the catalyst for decomposing organic substances that satisfies the requirements of the present invention can suppress a decrease in activity when used in a high temperature environment such as 800 ° C.
  • This catalyst for decomposing organic substances can be used for various purposes for decomposing organic substances, such as purification of exhaust gas from factories and automobiles. In that case, it can be configured as an organic matter decomposition apparatus provided with a catalyst for organic matter decomposition that satisfies the requirements of the present invention.
  • the organic substance to be decomposed is, for example, toluene.
  • toluene When toluene is steam reformed using the organic matter decomposition catalyst according to the present invention, H 2 is adsorbed on the organic matter decomposition catalyst. Therefore, by confirming the amount of H 2 adsorbed during the decomposition of toluene, the amount of decomposition and the decomposition rate of toluene, which is an organic substance, can be confirmed.
  • organic matter to be decomposed is not limited to toluene.
  • method of decomposing organic substances is not limited to steam reforming, and carbon dioxide may be used, for example.
  • the catalysts for decomposing organic substances of Examples 1 to 8 described below are catalysts that satisfy the above-mentioned requirements of the present invention.
  • the carrier is made of aluminum nitride having an atomic% ratio N / Al of N and Al existing on the surface of 0.40 or more and 0.50 or less. Further, the catalysts for organic matter decomposition of Examples 1 to 8 do not contain chlorine.
  • Example 1 The catalyst for organic matter decomposition of Example 1 was prepared by the following procedures 1 to 3.
  • Bisacetylacetonate platinum (II) was dissolved in toluene by ultrasonic irradiation to prepare a solution having a platinum content of 1% by mass.
  • Bisacetylacetonate platinum (II) is a platinum salt whose chemical structure does not contain chlorine.
  • the H 2 gas was flowed into the measuring tube for 120 seconds and injected into the sample tube 10 seconds later.
  • the judgment value of pulse detection was 0.001 mV / sec, and it was judged that the adsorption equilibrium was reached within 1.2% of the difference between the detectors of the final 3 pulses.
  • the amount of H 2 gas adsorbed and the degree of dispersion of platinum nanoparticles were determined.
  • "of H 2 gas” obtained by dividing the adsorption amount of H 2 gas by the mass of the catalyst for decomposition of organic substances both before and after the heat treatment at 800 ° C. according to operation 4.
  • a unit adsorption amount ", the amount of adsorption of H 2 gas were determined and obtained by dividing the mass of the platinum" H 2 gas adsorption amount per platinum mass ".
  • FIG. 1 shows a photograph when the surface of the catalyst for organic matter decomposition of Example 1 was observed at an observation magnification of 150,000 times.
  • platinum (platinum nanoparticles) 2 is supported on the carrier 1 of the organic matter decomposition catalyst 10. Further, as shown in FIG. 1, even after the heat treatment at a high temperature such as 800 ° C., the supported platinum nanoparticles are not coarsened due to excessive sintering and aggregation.
  • the observation magnification was set to 500,000 times, and 40 platinum nanoparticles from a plurality of fields of view were binarized using image analysis software. Was performed, and the equivalent circle diameter was measured. The average value of the measured 40 circle-equivalent diameters was calculated and used as the average particle size of the platinum nanoparticles.
  • Example 2 The organic matter decomposition catalyst of Example 2 was prepared by the same operations as in Operations 1 to 3 of Example 1 except that the target loading amount of platinum was adjusted to be 2% by mass. Further, the produced catalyst for decomposition of organic matter was heat-treated by the same method as the heat treatment method described in operation 4 of Example 1.
  • the amount of H 2 gas adsorbed and the degree of dispersion of platinum nanoparticles were determined by the same method as described in step 6 of Example 1. From the adsorption amount of H 2 gas was determined and the unit amount of adsorption of H 2 gas before and after the heat treatment is performed at 800 ° C., and H 2 gas adsorption amount per platinum mass.
  • Example 2 Further, the surface of the catalyst for organic matter decomposition of Example 2 was observed by the same method as that described in Operation 7 of Example 1. A photograph of the surface of the catalyst for decomposing organic matter of Example 2 is shown in FIG.
  • the average particle size of the supported platinum nanoparticles was determined by the same method as that described in operation 7 of Example 1.
  • Example 3 The organic matter decomposition catalyst of Example 3 was prepared by the same operations as in Operations 1 to 3 of Example 1 except that the target loading amount of platinum was adjusted to 3% by mass. Further, the produced catalyst for decomposition of organic matter was heat-treated by the same method as the heat treatment method described in operation 4 of Example 1.
  • the amount of H 2 gas adsorbed and the degree of dispersion of platinum nanoparticles were determined by the same method as described in step 6 of Example 1. From the adsorption amount of H 2 gas was determined and the unit amount of adsorption of H 2 gas before and after the heat treatment is performed at 800 ° C., and H 2 gas adsorption amount per platinum mass.
  • Example 3 Further, the surface of the catalyst for organic matter decomposition of Example 3 was observed by the same method as that described in Operation 7 of Example 1. A photograph of the surface of the catalyst for decomposing organic matter of Example 3 is shown in FIG.
  • the average particle size of the supported platinum nanoparticles was determined by the same method as that described in operation 7 of Example 1.
  • Example 4 The organic matter decomposition catalyst of Example 4 was prepared by the same operations as in Operations 1 to 3 of Example 1 except that the target loading amount of platinum was adjusted to 5% by mass. Further, the produced catalyst for decomposition of organic matter was heat-treated by the same method as the heat treatment method described in operation 4 of Example 1.
  • Example 4 The surface of the catalyst for organic matter decomposition of Example 4 was qualitatively and semi-quantitatively analyzed by the same method as that described in Operation 5 of Example 1. Table 2 shows the results of qualitative and semi-quantitative analysis of the elements.
  • the amount of H 2 gas adsorbed and the degree of dispersion of platinum nanoparticles were determined by the same method as described in step 6 of Example 1. Further, it determined from the adsorption amount of H 2 gas, and the unit amount of adsorption of H 2 gas before and after the heat treatment is performed at 800 ° C., and H 2 gas adsorption amount per platinum mass.
  • Example 4 Further, the surface of the catalyst for organic matter decomposition of Example 4 was observed by the same method as that described in Operation 7 of Example 1. A photograph of the surface of the catalyst for decomposing organic matter of Example 4 is shown in FIG.
  • the average particle size of the supported platinum nanoparticles was determined by the same method as that described in the above operation 7.
  • Example 5 The catalyst for organic matter decomposition of Example 5 was prepared by the following procedures from Operation 1A to Operation 3A.
  • Hexachloroplatinic acid (IV) acid / hexahydrate was dissolved in pure water by ultrasonic irradiation to prepare a solution having a platinum content of 1% by mass.
  • Hexachloroplatin (IV) acid / hexahydrate is a platinum salt whose chemical structure does not contain chlorine.
  • ⁇ Operation 2A> An aluminum nitride dispersion having a mass of 0.5 g and an average particle size of D50 of 1.2 ⁇ m was added to the above-mentioned solution in which hexachloride platinum (IV) acid / hexahydrate was dissolved to prepare an aluminum nitride dispersion. The amount of the solution was adjusted so that the target loading amount of platinum was 1% by mass. A beaker containing the aluminum nitride dispersion was placed on a hot stirrer, and the aluminum nitride solution was dried while stirring with a stirring rod at a set temperature of 100 ° C.
  • Example 5 After evaporating to dryness, the catalyst for organic matter decomposition of Example 5 was prepared by performing heat treatment under the same conditions and the same method as the heat treatment conditions of Operation 3 of Example 1.
  • Example 5 A qualitative and semi-quantitative analysis of the surface of the catalyst for organic matter decomposition of Example 5 was performed by the same method as that described in Operation 5 of Example 1. Table 4 shows the results of qualitative and semi-quantitative analysis of the elements.
  • ⁇ Operation 6A> The amount of H 2 gas adsorbed and the degree of dispersion of platinum nanoparticles supported on the carrier were determined by the same method as described in step 6 of Example 1. Further, it determined from the adsorption amount of H 2 gas, and the unit amount of adsorption of H 2 gas before and after the heat treatment is performed at 800 ° C., and H 2 gas adsorption amount per platinum mass.
  • Example 6 The organic matter decomposition catalyst of Example 6 was prepared by the same method as the organic matter decomposition catalyst of Example 5 except that the target carrying amount of platinum was adjusted to be 2% by mass. Further, the produced catalyst for decomposition of organic matter was heat-treated by the same method as the heat treatment method described in operation 4 of Example 1.
  • the amount of H 2 gas adsorbed and the degree of dispersion of platinum nanoparticles were determined by the same method as described in step 6 of Example 1. From the adsorption amount of H 2 gas was determined and the unit amount of adsorption of H 2 gas before and after the heat treatment is performed at 800 ° C., and H 2 gas adsorption amount per platinum mass.
  • Example 6 Further, the surface of the catalyst for organic matter decomposition of Example 6 was observed by the same method as that described in Operation 7 of Example 1. A photograph of the surface of the catalyst for decomposing organic matter of Example 6 is shown in FIG.
  • the average particle size of the supported platinum nanoparticles was determined by the same method as that described in operation 7 of Example 1.
  • Example 7 The organic matter decomposition catalyst of Example 7 was prepared by the same method as the organic matter decomposition catalyst of Example 5 except that the target carrying amount of platinum was adjusted to 3% by mass. Further, the produced catalyst for decomposition of organic matter was heat-treated by the same method as the heat treatment method described in operation 4 of Example 1.
  • the amount of H 2 gas adsorbed and the degree of dispersion of platinum nanoparticles were determined by the same method as described in step 6 of Example 1. From the adsorption amount of H 2 gas was determined and the unit amount of adsorption of H 2 gas before and after the heat treatment is performed at 800 ° C., and H 2 gas adsorption amount per platinum mass.
  • Example 8 The organic matter decomposition catalyst of Example 8 was prepared by the same method as the method for producing the organic matter decomposition catalyst of Example 5 except that the target carrying amount of platinum was adjusted to 5% by mass. Further, the produced catalyst for decomposition of organic matter was heat-treated by the same method as the heat treatment method described in operation 4 of Example 1.
  • the amount of H 2 gas adsorbed and the degree of dispersion of platinum nanoparticles were determined by the same method as described in step 6 of Example 1. From the adsorption amount of H 2 gas was determined and the unit amount of adsorption of H 2 gas before and after the heat treatment is performed at 800 ° C., and H 2 gas adsorption amount per platinum mass.
  • the catalysts for decomposition of organic substances of Comparative Examples 1 to 14 described below are catalysts that do not satisfy the above-mentioned requirements of the present invention.
  • Comparative Example 1 The catalyst for decomposition of organic matter of Comparative Example 1 was prepared by the following procedures 1B to 5B.
  • ⁇ Operation 2B> An aluminum nitride dispersion having a mass of 0.5 g and an average particle size of D50 of 1.2 ⁇ m was added to the above-mentioned solution in which hexachloride platinum (IV) acid / hexahydrate was dissolved to prepare an aluminum nitride dispersion. Then, the produced aluminum nitride dispersion was stirred with a stirrer at 300 rpm.
  • ⁇ Operation 3B> The aluminum nitride dispersion was solid-liquid separated using a membrane filter having a pore size of 1 ⁇ m. The surface of the powder existing on the surface of the membrane filter was washed by performing suction filtration three times with 20 mL of pure water.
  • ⁇ Operation 5B> The dried product obtained by the above operation 4B was transferred from an aluminum petri dish to a crucible and heat-treated in the atmosphere at 500 ° C. for 1 hour. Then, after taking out the crucible from the heat treatment furnace whose temperature was lowered to 100 ° C. or lower, the mixed gas flow in which the ratio of H 2 to N 2 (H 2 / N 2) was 3% again at 400 ° C. for 1 hour. By heat-treating underneath, a catalyst for decomposition of organic matter of Comparative Example 1 was prepared.
  • ⁇ Operation 6B> The surface of the produced catalyst for decomposition of organic matter was observed using a scanning electron microscope "HD-2300A” manufactured by Hitachi and an energy dispersive X-ray analyzer "Genesis XM4" manufactured by EDAX. The observation photograph is shown in FIG. By observing the surface of the catalyst for decomposition of organic matter, it was confirmed that platinum nanoparticles having a size of about 5 nm were uniformly supported on the surface of aluminum nitride.
  • ⁇ Operation 8B> The catalyst for decomposition of organic matter was recovered from the crucible, and 0.1 g was added to the sample tube. Then, the catalyst for decomposition of organic substances is desorbed from adsorbents such as water at 400 ° C. using a catalyst analyzer "BELCAT" manufactured by Microtrac Bell, cooled to 50 ° C., and then subjected to a pulse chemisorption method. , The amount of H 2 gas adsorbed and the degree of dispersion of platinum nanoparticles supported on the carrier were determined. In the pulse chemisorption method, Ar was used as the carrier gas, and H 2 gas having a concentration of 5% by volume was repeatedly introduced in a pulse shape. The flow rate of the introduced gas is 30 cm 3 / min, and the measurement temperature stabilization time is 15 minutes.
  • the H 2 gas was flowed into the measuring tube for 120 seconds and injected into the sample tube 10 seconds later.
  • the judgment value of pulse detection was 0.001 mV / sec, and it was judged that the adsorption equilibrium was reached within 1.2% of the difference between the detectors of the final 3 pulses.
  • the amount of H 2 gas adsorbed and the degree of dispersion of platinum nanoparticles were determined. Again, before performing the heat treatment at 800 ° C.
  • the adsorption amount of H 2 gas obtained by dividing by the mass of organic decomposition catalyst "of the H 2 gas a unit adsorption amount ", the amount of adsorption of H 2 gas were determined and obtained by dividing the mass of the platinum" H 2 gas adsorption amount per platinum mass ".
  • Comparative Example 2 The catalyst for decomposition of organic matter of Comparative Example 2 was prepared by the following procedures 1C to 5C.
  • the concentration of the reducing agent is 85 g / L.
  • the prepared reducing agent was slowly added dropwise to the aluminum nitride dispersion using a micropipette. The dropping of the reducing agent caused vigorous foaming, and the yellowish aluminum nitride dispersion instantly turned gray. After defoaming, the aluminum nitride dispersion was stirred for 2 hours.
  • ⁇ Operation 4C> The aluminum nitride dispersion was solid-liquid separated using a membrane filter having a pore size of 1 ⁇ m. The surface of the powder existing on the surface of the membrane filter was washed by performing suction filtration three times with 20 mL of ethanol.
  • FIG. 7A is a photograph when the observation magnification is 100,000 times
  • FIG. 7B is a photograph when the observation magnification is 600,000 times.
  • ⁇ Operation 8C> The amount of H 2 gas adsorbed and the degree of dispersion of platinum nanoparticles supported on the carrier were determined by the same method as described in Operation 8B of Comparative Example 1. Further, it determined from the adsorption amount of H 2 gas, and the unit amount of adsorption of H 2 gas before and after the heat treatment is performed at 800 ° C., and H 2 gas adsorption amount per platinum mass.
  • Comparative Example 3 The catalyst for organic matter decomposition of Comparative Example 3 was produced by the following procedures from Operation 1D to Operation 5D.
  • an aluminum nitride dispersion having a mass of 1 g and an average particle size of D50 of 1.2 ⁇ m was added to the above-mentioned pH-adjusted solution to prepare an aluminum nitride dispersion.
  • a beaker containing the aluminum nitride dispersion was placed on a hot stirrer, and the aluminum nitride dispersion was dried while stirring with a stirring rod at a set temperature of 100 ° C.
  • FIG. 6D The surface of the produced catalyst for decomposition of organic matter was observed by the same method as that described in Operation 6B of Comparative Example 1.
  • the observation photograph is shown in FIG. FIG. 8A is a photograph when the observation magnification is 150,000 times, and FIG. 8B is a photograph when the observation magnification is 600,000 times.
  • ⁇ Operation 8D> The amount of H 2 gas adsorbed and the degree of dispersion of platinum nanoparticles supported on the carrier were determined by the same method as described in Operation 8B of Comparative Example 1. Further, it determined from the adsorption amount of H 2 gas, and the unit amount of adsorption of H 2 gas before and after the heat treatment is performed at 800 ° C., and H 2 gas adsorption amount per platinum mass.
  • Comparative Example 4 The catalyst for decomposition of organic matter of Comparative Example 4 was prepared by the following procedures from Operation 1E to Operation 5E.
  • ⁇ Operation 2E> 1.23 mL of 1 M aqueous sodium hydroxide solution was added to the solution in which hexachloride platinum (IV) acid / hexahydrate was dissolved. The pH of this solution was measured using a pH meter manufactured by HORIBA, Ltd. and found to be 7.09.
  • an aluminum nitride dispersion having a mass of 1 g and an average particle size of D50 of 1.2 ⁇ m was added to the above-mentioned pH-adjusted solution to prepare an aluminum nitride dispersion.
  • a beaker containing the aluminum nitride dispersion was placed on a hot stirrer, and the aluminum nitride dispersion was dried while stirring with a stirring rod at a set temperature of 100 ° C.
  • ⁇ Operation 8E> The amount of H 2 gas adsorbed and the degree of dispersion of platinum nanoparticles supported on the carrier were determined by the same method as described in Operation 8B of Comparative Example 1. Further, it determined from the adsorption amount of H 2 gas, and the unit amount of adsorption of H 2 gas before and after the heat treatment is performed at 800 ° C., and H 2 gas adsorption amount per platinum mass.
  • Comparative Example 5 The catalyst for organic matter decomposition of Comparative Example 5 was produced by the following procedures from Operation 1F to Operation 5F.
  • ⁇ Operation 2F> 1.30 mL of a 1 M aqueous sodium hydroxide solution was added to a solution in which hexachloride platinum (IV) acid / hexahydrate was dissolved. The pH of this solution was measured using a pH meter manufactured by HORIBA, Ltd. and found to be 12.43.
  • an aluminum nitride dispersion having a mass of 1 g and an average particle size of D50 of 1.2 ⁇ m was added to the above-mentioned pH-adjusted solution to prepare an aluminum nitride dispersion.
  • a beaker containing the aluminum nitride dispersion was placed on a hot stirrer, and the aluminum nitride dispersion was dried while stirring with a stirring rod at a set temperature of 100 ° C.
  • ⁇ Operation 8F> The amount of H 2 gas adsorbed and the degree of dispersion of platinum nanoparticles supported on the carrier were determined by the same method as described in Operation 8B of Comparative Example 1. Further, it determined from the adsorption amount of H 2 gas, and the unit amount of adsorption of H 2 gas before and after the heat treatment is performed at 800 ° C., and H 2 gas adsorption amount per platinum mass.
  • Comparative Example 6 The catalyst for organic matter decomposition of Comparative Example 6 was produced by the following procedures from Operation 1G to Operation 3G.
  • ⁇ Operation 2G> An ⁇ -alumina dispersion was prepared by adding 0.5 g of ⁇ -alumina powder having a particle size of about 2 to 3 ⁇ m to the solution in which the above-mentioned hexachloride platinum (IV) acid / hexahydrate was dissolved. The amount of the solution was adjusted so that the target loading amount of platinum was 1% by mass. Then, a beaker containing the ⁇ -alumina dispersion was placed on a hot stirrer, and the ⁇ -alumina dispersion was dried while stirring with a stirring rod at a set temperature of 100 ° C.
  • ⁇ Operation 5G> The amount of H 2 gas adsorbed and the degree of dispersion of platinum nanoparticles supported on the carrier were determined by the same method as described in Operation 8B of Comparative Example 1. Further, it determined from the adsorption amount of H 2 gas, and the unit amount of adsorption of H 2 gas before and after the heat treatment is performed at 800 ° C., and H 2 gas adsorption amount per platinum mass.
  • Comparative Example 7 The organic matter decomposition catalyst of Comparative Example 7 was prepared by the same method as the method for producing the organic matter decomposition catalyst of Comparative Example 6 except that the target carrying amount of platinum was adjusted to be 2% by mass. Further, the produced catalyst for decomposition of organic matter was heat-treated by the same method as the heat treatment method described in operation 7B of Comparative Example 1.
  • FIG. 11 shows a photograph of Comparative Example 7 when the surface of the catalyst for decomposition of organic matter was observed.
  • the amount of H 2 gas adsorbed and the degree of dispersion of platinum nanoparticles supported on the carrier were determined by the same method as described in Operation 8B of Comparative Example 1. Further, it determined from the adsorption amount of H 2 gas, and the unit amount of adsorption of H 2 gas before and after the heat treatment is performed at 800 ° C., and H 2 gas adsorption amount per platinum mass.
  • the average particle size of the supported platinum nanoparticles was determined by the same method as that described in operation 7 of Example 1.
  • Comparative Example 8 The organic matter decomposition catalyst of Comparative Example 8 was prepared by the same method as the method for producing the organic matter decomposition catalyst of Comparative Example 6 except that the target carrying amount of platinum was adjusted to 3% by mass. Further, the produced catalyst for decomposition of organic matter was heat-treated by the same method as the heat treatment method described in operation 7B of Comparative Example 1.
  • the amount of H 2 gas adsorbed and the degree of dispersion of platinum nanoparticles supported on the carrier were determined by the same method as described in Operation 8B of Comparative Example 1. Further, it determined from the adsorption amount of H 2 gas, and the unit amount of adsorption of H 2 gas before and after the heat treatment is performed at 800 ° C., and H 2 gas adsorption amount per platinum mass.
  • Comparative Example 9 The organic matter decomposition catalyst of Comparative Example 9 was prepared by the same method as the method for producing the organic matter decomposition catalyst of Comparative Example 6 except that the target carrying amount of platinum was adjusted to 5% by mass. Further, the produced catalyst for decomposition of organic matter was heat-treated by the same method as the heat treatment method described in operation 7B of Comparative Example 1.
  • the amount of H 2 gas adsorbed and the degree of dispersion of platinum nanoparticles supported on the carrier were determined by the same method as described in Operation 8B of Comparative Example 1. Further, it determined from the adsorption amount of H 2 gas, and the unit amount of adsorption of H 2 gas before and after the heat treatment is performed at 800 ° C., and H 2 gas adsorption amount per platinum mass.
  • Comparative Example 10 The catalyst for organic matter decomposition of Comparative Example 10 was prepared by the following procedures from Operation 1H to Operation 3H.
  • the catalyst for decomposition of organic matter in Comparative Example 10 corresponds to the catalyst of Example 19 described in JP-A-2003-144933.
  • Aluminum nitride powder having an average particle size D50 of 1.2 ⁇ m was heat-treated at 1000 ° C. for 2 hours under atmospheric conditions. 0.5 g of the heat-treated aluminum nitride powder was added to the above-mentioned solution in which the hexachloride platinum (IV) acid / hexahydrate was dissolved to prepare an aluminum nitride dispersion. The amount of the solution was adjusted so that the target loading amount of platinum was 0.5% by mass. A beaker containing the aluminum nitride dispersion was placed on a hot stirrer, and the aluminum nitride dispersion was dried while stirring with a stirring rod at a set temperature of 100 ° C.
  • a catalyst for decomposition of organic substances of Comparative Example 10 was prepared by performing a heat treatment in the same manner as the heat treatment method described in Operation 5B of Comparative Example 1.
  • Comparative Example 11 The organic matter decomposition catalyst of Comparative Example 11 was prepared by the same method as the method for producing the organic matter decomposition catalyst of Comparative Example 10 except that the target carrying amount of platinum was adjusted to 1% by mass. Further, the produced catalyst for decomposition of organic matter was heat-treated by the same method as the heat treatment method described in operation 7B of Comparative Example 1.
  • the amount of H 2 gas adsorbed and the degree of dispersion of platinum nanoparticles supported on the carrier were determined by the same method as described in Operation 8B of Comparative Example 1. Further, it determined from the adsorption amount of H 2 gas, and the unit amount of adsorption of H 2 gas before and after the heat treatment is performed at 800 ° C., and H 2 gas adsorption amount per platinum mass.
  • Comparative Example 12 The organic matter decomposition catalyst of Comparative Example 12 was prepared by the same method as the method for producing the organic matter decomposition catalyst of Comparative Example 10 except that the target carrying amount of platinum was adjusted to be 2% by mass. Further, the produced catalyst for decomposition of organic matter was heat-treated by the same method as the heat treatment method described in operation 7B of Comparative Example 1.
  • the amount of H 2 gas adsorbed and the degree of dispersion of platinum nanoparticles supported on the carrier were determined by the same method as described in Operation 8B of Comparative Example 1. Further, it determined from the adsorption amount of H 2 gas, and the unit amount of adsorption of H 2 gas before and after the heat treatment is performed at 800 ° C., and H 2 gas adsorption amount per platinum mass.
  • Comparative Example 13 The organic matter decomposition catalyst of Comparative Example 13 was prepared by the same method as the method for producing the organic matter decomposition catalyst of Comparative Example 10 except that the target carrying amount of platinum was adjusted to be 3% by mass. Further, the produced catalyst for decomposition of organic matter was heat-treated by the same method as the heat treatment method described in operation 7B of Comparative Example 1.
  • the amount of H 2 gas adsorbed and the degree of dispersion of platinum nanoparticles supported on the carrier were determined by the same method as described in Operation 8B of Comparative Example 1. Further, it determined from the adsorption amount of H 2 gas, and the unit amount of adsorption of H 2 gas before and after the heat treatment is performed at 800 ° C., and H 2 gas adsorption amount per platinum mass.
  • Comparative Example 14 The organic matter decomposition catalyst of Comparative Example 14 was prepared by the same method as the method for producing the organic matter decomposition catalyst of Comparative Example 10 except that the target carrying amount of platinum was adjusted to 5% by mass. Further, the produced catalyst for decomposition of organic matter was heat-treated by the same method as the heat treatment method described in operation 7B of Comparative Example 1. The catalyst for decomposition of organic matter of Comparative Example 14 corresponds to the catalyst of Example 20 described in JP-A-2003-144933.
  • Comparative Example 14 The surface of the catalyst for organic matter decomposition of Comparative Example 14 was qualitatively and semi-quantitatively analyzed by the same method as that described in Operation 5 of Example 1. Table 7 shows the results of qualitative and semi-quantitative analysis of the elements.
  • the amount of H 2 gas adsorbed and the degree of dispersion of platinum nanoparticles supported on the carrier were determined by the same method as described in Operation 8B of Comparative Example 1. Further, it determined from the adsorption amount of H 2 gas, and the unit amount of adsorption of H 2 gas before and after the heat treatment is performed at 800 ° C., and H 2 gas adsorption amount per platinum mass.
  • the atomic% ratio N / Al of N and Al present on the surface of the carrier of the catalyst for organic matter decomposition of Examples 1, 4, 5, and 8 is 0.40 or more and 0.50 or less. ..
  • the atomic% ratio N / Al of N and Al present on the surface of the carrier of the catalyst for organic matter decomposition of Examples 2, 3, 6 and 7 is 0.40 or more and 0.50. It was also confirmed that it was as follows. Further, not only the organic matter decomposition catalysts of Comparative Examples 10 and 14 but also the atomic% ratio N / Al of N and Al present on the surface of the carrier of the organic matter decomposition catalysts of Comparative Examples 1 to 9 and 11 to 13 was 0. It was also confirmed that it was out of the range of 40 or more and 0.50 or less.
  • the target loading amount of platinum the adsorption amount of H 2 gas unit after heat treatment at 800 ° C., the adsorption amount of H 2 gas per platinum mass, and the heat treatment.
  • H 2 gas adsorption amount per H 2 gas unit adsorption amount and the platinum mass before, and show a reduction rate of the H 2 gas adsorption amount per platinum mass by annealing 800 ° C.
  • Table 9 the target loading amount of platinum, the adsorption amount of H 2 gas unit after heat treatment at 800 ° C., the adsorption amount of H 2 gas per platinum mass, and the heat treatment.
  • the catalysts for organic matter decomposition of Comparative Examples 1 to 14 which do not satisfy the requirements of the present invention have a reduction rate of H 2 gas adsorption amount per platinum mass of 94% or more before and after the heat treatment at 800 ° C. I grew up.
  • the reduction rate of the amount of H 2 gas adsorbed per platinum mass before and after the heat treatment at 800 ° C. is 61% or more and 94% or less. It was.
  • the catalysts for decomposing organic substances of Examples 1 to 8 satisfying the requirements of the present invention suppress the decrease in the amount of H 2 gas adsorbed when used in a high temperature environment such as 800 ° C., and decrease the catalytic activity. Can be suppressed.
  • Example 1 organic decomposition catalyst of 1-8, 800 H 2 gas adsorption amount per platinum mass in after heat treatment at °C is 0.46 cm 3 / g or more 1.61cm 3 / It is less than or equal to g.
  • Table 11 shows the target loading amount of platinum and the average particle size of platinum particles for the catalysts for organic matter decomposition in Examples 1 to 4, 6 and Comparative Examples 1 to 5, 7.
  • the standard deviation, the minimum value, and the maximum value of the particle size of the platinum particles are also shown.
  • the average particle size of the platinum particles of the catalysts for organic matter decomposition in Examples 1 to 4 and 6 is 28 nm or more and 41 nm or less. It has also been confirmed that the average particle size of the platinum particles of the catalysts for decomposition of organic substances in Examples 5, 7 and 8 is 28 nm or more and 41 nm or less.
  • FIG. 12 is a diagram showing the relationship between the average particle size of platinum particles of the catalysts for organic matter decomposition of Examples 1 to 4 and Comparative Examples 1 to 5 and the amount of H 2 gas adsorbed per platinum mass after heat treatment at 800 ° C. Is.
  • the organic matter decomposition catalysts of Examples 1 to 4 satisfying the requirements of the present invention have a temperature of 800 ° C. as compared with the organic matter decomposition catalysts of Comparative Examples 1 to 5 which do not satisfy the requirements of the present invention. It can be seen that the amount of H 2 gas adsorbed per platinum mass after the heat treatment is large.
  • FIG. 13 shows the organic substances of Comparative Examples having the same amount of platinum supported as the amount of H 2 gas adsorbed per platinum mass after heat treatment at 800 ° C. for the catalysts for decomposition of organic substances of Examples 1 to 8 and Comparative Examples 6 to 9.
  • FIG. 13 shows the organic substances of Comparative Examples having the same amount of platinum supported as the amount of H 2 gas adsorbed per platinum mass after heat treatment at 800 ° C. for the catalysts for decomposition of organic substances of Examples 1 to 8 and Comparative Examples 6 to 9.
  • FIG. 13 shows the organic substances of Comparative Examples having the same amount of platinum supported as the amount of H 2 gas adsorbed per platinum mass after heat treatment at 800 ° C. for the catalysts for decomposition of organic substances of Examples 1 to 8 and Comparative Examples 6 to 9.
  • the amount of platinum supported equivalent to their organic decomposition catalyst It is represented by K1 / K2 when the amount of H 2 gas unit adsorbed after the heat treatment of the organic substance decomposition catalyst of Comparative Example (any of Comparative Examples 6 to 9) at 800 ° C. is K2.
  • the ratio P1 of the H 2 gas unit adsorption amount for the organic matter decomposition catalysts of Comparative Examples 6 to 9 is 1.
  • FIG. 14 shows the organic substances of Comparative Examples of Examples 1 to 8 and Comparative Examples 11 to 14 having the same amount of H 2 gas adsorbed per platinum mass after heat treatment at 800 ° C. and the same amount of platinum supported. It is a figure which shows the relationship with the ratio P2 of the H 2 gas unit adsorption amount after the heat treatment at 800 degreeC when compared with the decomposition catalyst.
  • the H 2 gas unit adsorption ratio P2 is H 2 gas unit amount of adsorption after heat treatment 800 ° C.
  • the amount of platinum supported equivalent to their organic decomposition catalyst It is represented by K1 / K3 when the amount of H 2 gas unit adsorbed after the heat treatment of the organic substance decomposition catalyst of Comparative Example (any of Comparative Examples 11 to 14) at 800 ° C. is K3.
  • the ratio P2 of the H 2 gas unit adsorption amount for the organic matter decomposition catalysts of Comparative Examples 11 to 14 is 1.
  • the organic matter decomposition catalysts of Examples 1 to 8 satisfying the requirements of the present invention adsorb H 2 gas units after heat treatment at 800 ° C. as compared with the organic matter decomposition catalysts of Comparative Examples 11 to 14. The amount is large.
  • platinum nanoparticles that do not easily oxidize are supported on one surface of aluminum nitride contained in the carrier with a high degree of dispersion, so that the catalyst can be used in a high temperature environment such as 800 ° C. Even if it is used, it can suppress the oxidation of aluminum nitride. Therefore, since the thermal conductivity of aluminum nitride is maintained, heat dissipation proceeds even when the aluminum nitride is used in a high temperature environment, and the sintering of the supported platinum can be suppressed. Thereby, the decrease in the dispersity of platinum can be suppressed (sintering can be suppressed), and the decrease in the catalytic activity can be suppressed.
  • the average particle size of the platinum particles of the catalysts for organic matter decomposition of Examples 1 to 8 satisfying the requirements of the present invention is 28 nm or more and 41 nm or less. Therefore, in the catalyst for organic matter decomposition that satisfies the requirements of the present invention, it is preferable that the average particle size of platinum particles is 28 nm or more and 41 nm or less.

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Abstract

This organic matter decomposition catalyst for decomposing organic matter is provided with a carrier and platinum supported on the carrier. The carrier contains, at the surface thereof, an aluminum nitride in which the atomic% ratio N/Al of N and Al is 0.40-0.50.

Description

有機物分解用触媒および有機物分解装置Organic matter decomposition catalyst and organic matter decomposition equipment
 本発明は、有機物を分解するために用いられる有機物分解用触媒、および、有機物分解用触媒を備えた有機物分解装置に関する。 The present invention relates to an organic matter decomposition catalyst used for decomposing an organic substance and an organic matter decomposition apparatus provided with an organic matter decomposition catalyst.
 従来、有機物を分解するために用いられる有機物分解用触媒が知られている。 Conventionally, catalysts for decomposing organic substances used for decomposing organic substances are known.
 特許文献1には、金属または金属酸化物からなる金属触媒が窒化アルミニウムからなる担体に担持されている触媒が記載されている。この触媒は、高い機械的強度を有し、かつ、高い熱伝導度を有すると特許文献1には記載されている。 Patent Document 1 describes a catalyst in which a metal catalyst made of a metal or a metal oxide is supported on a carrier made of aluminum nitride. Patent Document 1 describes that this catalyst has high mechanical strength and high thermal conductivity.
 特許文献1に記載の触媒は、以下の方法により作製されている。まず、窒化アルミニウム粉末を、空気または酸素存在下で、900℃~1000℃で焼成し、窒化アルミニウム粒子の表面に酸化アルミニウム層を形成させる。続いて、銅金属粒子を含む水溶液に窒化アルミニウム粒子を含浸させた後、乾燥させることにより、窒化アルミニウムの表面に銅微粒子を担持させた触媒を得る。その後、得られた触媒を350℃~600℃の温度範囲において焼成させて、触媒粒子を得ている。 The catalyst described in Patent Document 1 is produced by the following method. First, the aluminum nitride powder is calcined at 900 ° C. to 1000 ° C. in the presence of air or oxygen to form an aluminum oxide layer on the surface of the aluminum nitride particles. Subsequently, the aqueous solution containing the copper metal particles is impregnated with the aluminum nitride particles and then dried to obtain a catalyst in which the copper fine particles are supported on the surface of the aluminum nitride. Then, the obtained catalyst is calcined in a temperature range of 350 ° C. to 600 ° C. to obtain catalyst particles.
特開2003-144933号公報Japanese Unexamined Patent Publication No. 2003-144933
 上述したように、特許文献1に記載の触媒は、窒化アルミニウム粒子の表面に酸化アルミニウム層が形成されているが、酸化アルミニウム層は、窒化アルミニウムよりも熱伝導率が低いため、担体の熱伝導率が低下する。このため、触媒が高温環境下で使用された際に放熱が十分進まず、担持されている金属微粒子の焼結が容易に進行してしまい、触媒の活性が低下する可能性がある。 As described above, in the catalyst described in Patent Document 1, an aluminum oxide layer is formed on the surface of the aluminum nitride particles, but the aluminum oxide layer has a lower thermal conductivity than the aluminum nitride, so that the thermal conductivity of the carrier is low. The rate drops. Therefore, when the catalyst is used in a high temperature environment, heat dissipation does not proceed sufficiently, and sintering of the supported metal fine particles easily proceeds, which may reduce the activity of the catalyst.
 本発明は、上記課題を解決するものであり、高温環境下で使用された場合の触媒活性の低下を抑制することができる有機物分解用触媒、および、そのような有機物分解用触媒を備えた有機物分解装置を提供することを目的とする。 The present invention solves the above-mentioned problems, and an organic substance decomposition catalyst capable of suppressing a decrease in catalytic activity when used in a high temperature environment, and an organic substance provided with such an organic substance decomposition catalyst. It is an object of the present invention to provide a disassembling device.
 本発明の有機物分解用触媒は、有機物を分解するために用いられる有機物分解用触媒であって、担体と、前記担体に担持された白金と、を備え、前記担体は、その表面に存在するNとAlの原子%比N/Alが0.40以上0.50以下である窒化アルミニウムを含むことを特徴とする。 The catalyst for decomposing an organic substance of the present invention is a catalyst for decomposing an organic substance used for decomposing an organic substance, and comprises a carrier and platinum supported on the carrier, and the carrier is present on the surface of N. It is characterized by containing aluminum nitride having an atomic% ratio N / Al of 0.40 or more and 0.50 or less.
 本発明の有機物分解用触媒によれば、高温環境下で使用された場合の触媒活性の低下を抑制することができる。 According to the catalyst for decomposing organic substances of the present invention, it is possible to suppress a decrease in catalytic activity when used in a high temperature environment.
実施例1の有機物分解用触媒の表面を観察したときの写真を示す図である。It is a figure which shows the photograph when the surface of the catalyst for organic matter decomposition of Example 1 was observed. 実施例2の有機物分解用触媒の表面を観察したときの写真を示す図である。It is a figure which shows the photograph at the time of observing the surface of the catalyst for organic matter decomposition of Example 2. 実施例3の有機物分解用触媒の表面を観察したときの写真を示す図である。It is a figure which shows the photograph at the time of observing the surface of the catalyst for organic matter decomposition of Example 3. 実施例4の有機物分解用触媒の表面を観察したときの写真を示す図である。It is a figure which shows the photograph at the time of observing the surface of the catalyst for organic matter decomposition of Example 4. 実施例6の有機物分解用触媒の表面を観察したときの写真を示す図である。It is a figure which shows the photograph at the time of observing the surface of the catalyst for organic matter decomposition of Example 6. 比較例1の有機物分解用触媒の表面を観察したときの写真を示す図である。It is a figure which shows the photograph at the time of observing the surface of the catalyst for organic matter decomposition of Comparative Example 1. 比較例2の有機物分解用触媒の表面を観察したときの写真を示す図であって、(a)は、観察倍率を10万倍としたときの写真であり、(b)は、観察倍率を60万倍としたときの写真を示す。It is a figure which shows the photograph when the surface of the catalyst for organic matter decomposition of the comparative example 2 was observed, (a) is the photograph when the observation magnification is 100,000 times, (b) is the observation magnification. The photograph when it is multiplied by 600,000 is shown. 比較例3の有機物分解用触媒の表面を観察したときの写真を示す図であって、(a)は、観察倍率を15万倍としたときの写真であり、(b)は、観察倍率を60万倍としたときの写真を示す。It is a figure which shows the photograph when the surface of the catalyst for organic matter decomposition of the comparative example 3 was observed, (a) is the photograph when the observation magnification is 150,000 times, (b) is the observation magnification. The photograph when it is multiplied by 600,000 is shown. 比較例4の有機物分解用触媒の表面を観察したときの写真を示す図である。It is a figure which shows the photograph at the time of observing the surface of the catalyst for organic matter decomposition of Comparative Example 4. 比較例5の有機物分解用触媒の表面を観察したときの写真を示す図である。It is a figure which shows the photograph at the time of observing the surface of the catalyst for organic matter decomposition of Comparative Example 5. 比較例7の有機物分解用触媒の表面を観察したときの写真を示す図である。It is a figure which shows the photograph at the time of observing the surface of the catalyst for organic matter decomposition of Comparative Example 7. 実施例1~4と比較例1~5の有機物分解用触媒の白金粒子の平均粒径と、800℃の熱処理後における白金質量あたりのH2ガス吸着量との関係を示す図である。It is a figure which shows the relationship between the average particle diameter of platinum particles of the catalyst for organic matter decomposition of Examples 1 to 4 and Comparative Examples 1 to 5, and the amount of H 2 gas adsorbed per platinum mass after heat treatment at 800 degreeC. 実施例1~8と比較例6~9の有機物分解用触媒について、800℃の熱処理後における白金質量あたりのH2ガス吸着量と、同等の白金担持量を有する比較例の有機物分解用触媒と比べたときに、800℃の熱処理後におけるH2ガス単位吸着量の比との関係を示す図である。Regarding the organic matter decomposition catalysts of Examples 1 to 8 and Comparative Examples 6 to 9, the organic matter decomposition catalysts of Comparative Examples having the same amount of H 2 gas adsorbed per platinum mass and the same amount of platinum supported after heat treatment at 800 ° C. It is a figure which shows the relationship with the ratio of the H 2 gas unit adsorption amount after the heat treatment at 800 degreeC when compared. 実施例1~8と比較例11~14の有機物分解用触媒について、800℃の熱処理後における白金質量あたりのH2ガス吸着量と、同等の白金担持量を有する比較例の有機物分解用触媒と比べたときに、800℃の熱処理後におけるH2ガス単位吸着量の比との関係を示す図である。Regarding the organic matter decomposition catalysts of Examples 1 to 8 and Comparative Examples 11 to 14, the organic matter decomposition catalysts of Comparative Examples having the same amount of H 2 gas adsorbed per platinum mass and the same amount of platinum supported after heat treatment at 800 ° C. It is a figure which shows the relationship with the ratio of the H 2 gas unit adsorption amount after the heat treatment at 800 degreeC when compared.
 以下に本発明の実施形態を示して、本発明の特徴を具体的に説明する。 Hereinafter, embodiments of the present invention will be shown, and the features of the present invention will be specifically described.
 本発明による有機物分解用触媒は、有機物を分解するために用いられる有機物分解用触媒であって、担体と、担体に担持された白金とを備え、担体は、その表面に存在するNとAlの原子%比N/Alが0.40以上0.50以下である窒化アルミニウムを含むという要件(以下、本発明の要件と呼ぶ)を満たす。 The catalyst for decomposing an organic substance according to the present invention is a catalyst for decomposing an organic substance used for decomposing an organic substance, and comprises a carrier and platinum supported on the carrier, and the carrier is composed of N and Al existing on the surface thereof. It satisfies the requirement of containing aluminum nitride having an atomic% ratio N / Al of 0.40 or more and 0.50 or less (hereinafter, referred to as the requirement of the present invention).
 本発明の要件を満たす有機物分解用触媒は、後述するように、800℃のような高温環境下で使用された場合の活性の低下を抑制することができる。この有機物分解用触媒は、工場や自動車からの排ガスの浄化など、有機物を分解するための種々の用途に用いることができる。その場合、本発明の要件を満たす有機物分解用触媒を備えた有機物分解装置として構成することができる。 As will be described later, the catalyst for decomposing organic substances that satisfies the requirements of the present invention can suppress a decrease in activity when used in a high temperature environment such as 800 ° C. This catalyst for decomposing organic substances can be used for various purposes for decomposing organic substances, such as purification of exhaust gas from factories and automobiles. In that case, it can be configured as an organic matter decomposition apparatus provided with a catalyst for organic matter decomposition that satisfies the requirements of the present invention.
 分解対象である有機物は、例えばトルエンである。本発明による有機物分解用触媒を用いてトルエンの水蒸気改質を行うと、有機物分解用触媒にH2が吸着される。したがって、トルエン分解時のH2の吸着量を確認することにより、有機物であるトルエンの分解量および分解率を確認することができる。 The organic substance to be decomposed is, for example, toluene. When toluene is steam reformed using the organic matter decomposition catalyst according to the present invention, H 2 is adsorbed on the organic matter decomposition catalyst. Therefore, by confirming the amount of H 2 adsorbed during the decomposition of toluene, the amount of decomposition and the decomposition rate of toluene, which is an organic substance, can be confirmed.
 ただし、分解対象である有機物がトルエンに限定されることはない。また、有機物を分解する方法が水蒸気改質に限定されることはなく、例えば、二酸化炭素を用いてもよい。 However, the organic matter to be decomposed is not limited to toluene. Further, the method of decomposing organic substances is not limited to steam reforming, and carbon dioxide may be used, for example.
 以下で説明する実施例1~8の有機物分解用触媒は、上述した本発明の要件を満たす触媒である。なお、実施例1~8の有機物分解用触媒において、担体は、その表面に存在するNとAlの原子%比N/Alが0.40以上0.50以下である窒化アルミニウムからなる。また、実施例1~8の有機物分解用触媒には塩素が含まれない。 The catalysts for decomposing organic substances of Examples 1 to 8 described below are catalysts that satisfy the above-mentioned requirements of the present invention. In the catalysts for organic matter decomposition of Examples 1 to 8, the carrier is made of aluminum nitride having an atomic% ratio N / Al of N and Al existing on the surface of 0.40 or more and 0.50 or less. Further, the catalysts for organic matter decomposition of Examples 1 to 8 do not contain chlorine.
 (実施例1)
 以下の操作1~操作3の手順により、実施例1の有機物分解用触媒を作製した。
(Example 1)
The catalyst for organic matter decomposition of Example 1 was prepared by the following procedures 1 to 3.
 <操作1>
 ビスアセチルアセトナート白金(II)を超音波照射によってトルエンに溶解させ、白金の含有量が1質量%の溶液を作製した。ビスアセチルアセトナート白金(II)は、化学構造に塩素が含まれない白金塩である。
<Operation 1>
Bisacetylacetonate platinum (II) was dissolved in toluene by ultrasonic irradiation to prepare a solution having a platinum content of 1% by mass. Bisacetylacetonate platinum (II) is a platinum salt whose chemical structure does not contain chlorine.
 <操作2>
 質量0.5g、平均粒径D50が1.2μmである窒化アルミニウム粉を上述したビスアセチルアセトナート白金(II)が溶解した溶液に添加して、窒化アルミニウム分散液を作製した。溶液の量は、白金の目標担持量が1質量%となるように調整した。その後、窒化アルミニウム分散液を入れたビーカーをホットスターラー上に設置し、設定温度100℃で、窒化アルミニウム分散液を攪拌棒で攪拌しながら乾燥させた。
<Operation 2>
An aluminum nitride dispersion having a mass of 0.5 g and an average particle size of D50 of 1.2 μm was added to the above-mentioned solution in which bisacetylacetonate platinum (II) was dissolved to prepare an aluminum nitride dispersion. The amount of the solution was adjusted so that the target loading amount of platinum was 1% by mass. Then, a beaker containing the aluminum nitride dispersion was placed on a hot stirrer, and the aluminum nitride dispersion was dried while stirring with a stirring rod at a set temperature of 100 ° C.
 <操作3>
 蒸発乾固後、ビーカーの中に残った乾燥物をるつぼに添加し、るつぼを熱処理炉内に入れて、500℃、1時間、大気下の条件で熱処理した。その後、100℃以下の温度に低下させた熱処理炉内からるつぼを取り出し、再度、400℃、1時間、H2とN2の比(H2/N2)が3%である混合ガス流通下で熱処理を行うことによって、実施例1の有機物分解用触媒を作製した。
<Operation 3>
After evaporation to dryness, the dried product remaining in the beaker was added to the crucible, and the crucible was placed in a heat treatment furnace and heat-treated at 500 ° C. for 1 hour under atmospheric conditions. After that, the crucible was taken out from the heat treatment furnace whose temperature was lowered to 100 ° C. or lower, and again under mixed gas flow in which the ratio of H 2 to N 2 (H 2 / N 2) was 3% at 400 ° C. for 1 hour. The catalyst for organic matter decomposition of Example 1 was prepared by performing the heat treatment in.
 <操作4>
 作製した有機物分解用触媒を、800℃、2時間、大気下の条件で熱処理した。
<Operation 4>
The prepared catalyst for decomposition of organic matter was heat-treated at 800 ° C. for 2 hours under atmospheric conditions.
 <操作5>
 X線光電子分光法(XPS)によるワイドスキャンスペクトル測定によって、上記操作4による熱処理後の有機物分解用触媒の表面の定性・半定量分析を行った。測定領域は、φ100mmとし、分析深さは数nmとした。元素の定性・半定量分析結果を表1に示す。
<Operation 5>
By wide scan spectrum measurement by X-ray photoelectron spectroscopy (XPS), qualitative and semi-quantitative analysis of the surface of the catalyst for organic matter decomposition after heat treatment by the above operation 4 was performed. The measurement area was φ100 mm, and the analysis depth was several nm. Table 1 shows the results of qualitative and semi-quantitative analysis of the elements.
Figure JPOXMLDOC01-appb-T000001
Figure JPOXMLDOC01-appb-T000001
 <操作6>
 るつぼ内から有機物分解用触媒を回収し、試料管に0.02g添加した。その後、有機物分解用触媒に対して、マイクロトラック・ベル社製の触媒分析装置「BELCAT」を用いて、400℃で水分などの吸着質を脱着して50℃まで冷却後、パルス化学吸着法により、H2ガスの吸着量と、担体に担持させている白金ナノ粒子の分散度を求めた。パルス化学吸着法では、キャリアガスとしてArを用い、濃度5体積%のH2ガスをパルス状に繰り返し導入した。導入したガスの流量は、30cm3/分、測定温度安定時間は15分である。
<Operation 6>
The catalyst for decomposition of organic matter was recovered from the crucible, and 0.02 g was added to the sample tube. Then, the catalyst for decomposition of organic substances is desorbed from adsorbents such as water at 400 ° C. using a catalyst analyzer "BELCAT" manufactured by Microtrac Bell, cooled to 50 ° C., and then subjected to a pulse chemisorption method. , The amount of H 2 gas adsorbed and the degree of dispersion of platinum nanoparticles supported on the carrier were determined. In the pulse chemisorption method, Ar was used as the carrier gas, and H 2 gas having a concentration of 5% by volume was repeatedly introduced in a pulse shape. The flow rate of the introduced gas is 30 cm 3 / min, and the measurement temperature stabilization time is 15 minutes.
 H2ガスは、計量管内に120秒流し、10秒後に試料管に注入した。パルス検出の判断値は、0.001mV/秒とし、最終3パルスの検出器の差が1.2%以内で吸着平衡に至ったと判断した。これにより、H2ガスの吸着量と白金ナノ粒子の分散度を求めた。ここでは、操作4による800℃での熱処理を行う前と、熱処理を行った後の両方において、H2ガスの吸着量を、有機物分解用触媒の質量で除算して得られる「H2ガスの単位吸着量」と、H2ガスの吸着量を、白金の質量で除算して得られる「白金質量あたりのH2ガス吸着量」とを求めた。 The H 2 gas was flowed into the measuring tube for 120 seconds and injected into the sample tube 10 seconds later. The judgment value of pulse detection was 0.001 mV / sec, and it was judged that the adsorption equilibrium was reached within 1.2% of the difference between the detectors of the final 3 pulses. As a result, the amount of H 2 gas adsorbed and the degree of dispersion of platinum nanoparticles were determined. Here, "of H 2 gas " obtained by dividing the adsorption amount of H 2 gas by the mass of the catalyst for decomposition of organic substances both before and after the heat treatment at 800 ° C. according to operation 4. a unit adsorption amount ", the amount of adsorption of H 2 gas were determined and obtained by dividing the mass of the platinum" H 2 gas adsorption amount per platinum mass ".
 <操作7>
 上記操作4による熱処理後の有機物分解用触媒の表面を、日本電子社製の電界放射型透過電子顕微鏡「JEM-2200FS」と日立製のエネルギー分散型X線分析装置「NORAN System seven」を用いて観察した。観察倍率15万倍で実施例1の有機物分解用触媒の表面を観察したときの写真を図1に示す。図1に示すように、有機物分解用触媒10の担体1には、白金(白金ナノ粒子)2が担持されている。また、図1に示すように、800℃のような高温での熱処理後でも、担持されている白金ナノ粒子は過剰な焼結、凝集に伴う粗大化が生じていない。
<Operation 7>
Using the field emission transmission electron microscope "JEM-2200FS" manufactured by JEOL Ltd. and the energy dispersive X-ray analyzer "NORAN System seven" manufactured by Hitachi, the surface of the catalyst for organic matter decomposition after the heat treatment by the above operation 4 is used. Observed. FIG. 1 shows a photograph when the surface of the catalyst for organic matter decomposition of Example 1 was observed at an observation magnification of 150,000 times. As shown in FIG. 1, platinum (platinum nanoparticles) 2 is supported on the carrier 1 of the organic matter decomposition catalyst 10. Further, as shown in FIG. 1, even after the heat treatment at a high temperature such as 800 ° C., the supported platinum nanoparticles are not coarsened due to excessive sintering and aggregation.
 また、担持されている白金ナノ粒子の平均粒径を求めるため、観察倍率を50万倍として、複数視野の中から40個の白金ナノ粒子に対して、画像解析ソフトを用いて二値化処理を行い、円相当径を計測した。計測した40個の円相当径の平均値を求めて、白金ナノ粒子の平均粒径とした。 In addition, in order to obtain the average particle size of the supported platinum nanoparticles, the observation magnification was set to 500,000 times, and 40 platinum nanoparticles from a plurality of fields of view were binarized using image analysis software. Was performed, and the equivalent circle diameter was measured. The average value of the measured 40 circle-equivalent diameters was calculated and used as the average particle size of the platinum nanoparticles.
 (実施例2)
 白金の目標担持量が2質量%となるように調整したこと以外は、実施例1の操作1~操作3と同じ操作によって、実施例2の有機物分解用触媒を作製した。また、作製した有機物分解用触媒を、実施例1の操作4で説明した熱処理方法と同じ方法で熱処理した。
(Example 2)
The organic matter decomposition catalyst of Example 2 was prepared by the same operations as in Operations 1 to 3 of Example 1 except that the target loading amount of platinum was adjusted to be 2% by mass. Further, the produced catalyst for decomposition of organic matter was heat-treated by the same method as the heat treatment method described in operation 4 of Example 1.
 また、実施例1の操作6で説明した方法と同じ方法により、H2ガスの吸着量と白金ナノ粒子の分散度を求めた。H2ガスの吸着量から、800℃で熱処理を行う前後におけるH2ガスの単位吸着量と、白金質量あたりのH2ガス吸着量とを求めた。 In addition, the amount of H 2 gas adsorbed and the degree of dispersion of platinum nanoparticles were determined by the same method as described in step 6 of Example 1. From the adsorption amount of H 2 gas was determined and the unit amount of adsorption of H 2 gas before and after the heat treatment is performed at 800 ° C., and H 2 gas adsorption amount per platinum mass.
 また、実施例1の操作7で説明した方法と同じ方法により、実施例2の有機物分解用触媒の表面を観察した。実施例2の有機物分解用触媒の表面を観察したときの写真を図2に示す。 Further, the surface of the catalyst for organic matter decomposition of Example 2 was observed by the same method as that described in Operation 7 of Example 1. A photograph of the surface of the catalyst for decomposing organic matter of Example 2 is shown in FIG.
 また、実施例1の操作7で説明した方法と同じ方法により、担持されている白金ナノ粒子の平均粒径を求めた。 Further, the average particle size of the supported platinum nanoparticles was determined by the same method as that described in operation 7 of Example 1.
 (実施例3)
 白金の目標担持量が3質量%となるように調整したこと以外は、実施例1の操作1~操作3と同じ操作によって、実施例3の有機物分解用触媒を作製した。また、作製した有機物分解用触媒を、実施例1の操作4で説明した熱処理方法と同じ方法で熱処理した。
(Example 3)
The organic matter decomposition catalyst of Example 3 was prepared by the same operations as in Operations 1 to 3 of Example 1 except that the target loading amount of platinum was adjusted to 3% by mass. Further, the produced catalyst for decomposition of organic matter was heat-treated by the same method as the heat treatment method described in operation 4 of Example 1.
 また、実施例1の操作6で説明した方法と同じ方法により、H2ガスの吸着量と白金ナノ粒子の分散度を求めた。H2ガスの吸着量から、800℃で熱処理を行う前後におけるH2ガスの単位吸着量と、白金質量あたりのH2ガス吸着量とを求めた。 In addition, the amount of H 2 gas adsorbed and the degree of dispersion of platinum nanoparticles were determined by the same method as described in step 6 of Example 1. From the adsorption amount of H 2 gas was determined and the unit amount of adsorption of H 2 gas before and after the heat treatment is performed at 800 ° C., and H 2 gas adsorption amount per platinum mass.
 また、実施例1の操作7で説明した方法と同じ方法により、実施例3の有機物分解用触媒の表面を観察した。実施例3の有機物分解用触媒の表面を観察したときの写真を図3に示す。 Further, the surface of the catalyst for organic matter decomposition of Example 3 was observed by the same method as that described in Operation 7 of Example 1. A photograph of the surface of the catalyst for decomposing organic matter of Example 3 is shown in FIG.
 また、実施例1の操作7で説明した方法と同じ方法により、担持されている白金ナノ粒子の平均粒径を求めた。 Further, the average particle size of the supported platinum nanoparticles was determined by the same method as that described in operation 7 of Example 1.
 (実施例4)
 白金の目標担持量が5質量%となるように調整したこと以外は、実施例1の操作1~操作3と同じ操作によって、実施例4の有機物分解用触媒を作製した。また、作製した有機物分解用触媒を、実施例1の操作4で説明した熱処理方法と同じ方法で熱処理した。
(Example 4)
The organic matter decomposition catalyst of Example 4 was prepared by the same operations as in Operations 1 to 3 of Example 1 except that the target loading amount of platinum was adjusted to 5% by mass. Further, the produced catalyst for decomposition of organic matter was heat-treated by the same method as the heat treatment method described in operation 4 of Example 1.
 実施例1の操作5で説明した方法と同じ方法により、実施例4の有機物分解用触媒の表面の定性・半定量分析を行った。元素の定性・半定量分析結果を表2に示す。 The surface of the catalyst for organic matter decomposition of Example 4 was qualitatively and semi-quantitatively analyzed by the same method as that described in Operation 5 of Example 1. Table 2 shows the results of qualitative and semi-quantitative analysis of the elements.
Figure JPOXMLDOC01-appb-T000002
Figure JPOXMLDOC01-appb-T000002
 実施例1の操作6で説明した方法と同じ方法により、H2ガスの吸着量と白金ナノ粒子の分散度を求めた。また、H2ガスの吸着量から、800℃で熱処理を行う前後におけるH2ガスの単位吸着量と、白金質量あたりのH2ガス吸着量とを求めた。 The amount of H 2 gas adsorbed and the degree of dispersion of platinum nanoparticles were determined by the same method as described in step 6 of Example 1. Further, it determined from the adsorption amount of H 2 gas, and the unit amount of adsorption of H 2 gas before and after the heat treatment is performed at 800 ° C., and H 2 gas adsorption amount per platinum mass.
 また、実施例1の操作7で説明した方法と同じ方法により、実施例4の有機物分解用触媒の表面を観察した。実施例4の有機物分解用触媒の表面を観察したときの写真を図4に示す。 Further, the surface of the catalyst for organic matter decomposition of Example 4 was observed by the same method as that described in Operation 7 of Example 1. A photograph of the surface of the catalyst for decomposing organic matter of Example 4 is shown in FIG.
 また、上記操作7で説明した方法と同じ方法により、担持されている白金ナノ粒子の平均粒径を求めた。 Further, the average particle size of the supported platinum nanoparticles was determined by the same method as that described in the above operation 7.
 上述した実施例1~4の有機物分解用触媒のそれぞれを、酸処理によって溶解させた後、不溶分を濾過して、濾液中の白金の質量%を測定した。この白金の質量%は、担持されている白金の実際の担持量を意味する。白金の質量%の測定は、サーモフィッシャーサイエンティフィック社製のICP発光分析装置「iCAP6300」を用いて2回行い、その平均値を求めた。実施例1~4について、白金の目標担持量および白金の実際の担持量を表3に示す。 After dissolving each of the above-mentioned catalysts for decomposition of organic substances in Examples 1 to 4 by acid treatment, the insoluble matter was filtered, and the mass% of platinum in the filtrate was measured. The mass% of this platinum means the actual amount of platinum supported. The mass% of platinum was measured twice using an ICP emission spectrometer "iCAP6300" manufactured by Thermo Fisher Scientific Co., Ltd., and the average value was obtained. For Examples 1 to 4, the target carrier amount of platinum and the actual carrier amount of platinum are shown in Table 3.
Figure JPOXMLDOC01-appb-T000003
Figure JPOXMLDOC01-appb-T000003
 表3に示すように、白金の実際の担持量は、目標担持量と比べて大きく乖離していないことが分かった。 As shown in Table 3, it was found that the actual supported amount of platinum did not deviate significantly from the target supported amount.
 (実施例5)
 以下の操作1A~操作3Aの手順により、実施例5の有機物分解用触媒を作製した。
(Example 5)
The catalyst for organic matter decomposition of Example 5 was prepared by the following procedures from Operation 1A to Operation 3A.
 <操作1A>
 ヘキサクロリド白金(IV)酸・六水和物を超音波照射によって純水に溶解させ、白金の含有量が1質量%の溶液を作製した。ヘキサクロリド白金(IV)酸・六水和物は、化学構造に塩素が含まれない白金塩である。
<Operation 1A>
Hexachloroplatinic acid (IV) acid / hexahydrate was dissolved in pure water by ultrasonic irradiation to prepare a solution having a platinum content of 1% by mass. Hexachloroplatin (IV) acid / hexahydrate is a platinum salt whose chemical structure does not contain chlorine.
 <操作2A>
 質量0.5g、平均粒径D50が1.2μmである窒化アルミニウム粉を上述したヘキサクロリド白金(IV)酸・六水和物が溶解した溶液に添加して、窒化アルミニウム分散液を作製した。溶液の量は、白金の目標担持量が1質量%となるように調整した。窒化アルミニウム分散液を入れたビーカーを、ホットスターラー上に設置し、設定温度100℃で、窒化アルミニウム溶液を攪拌棒で攪拌しながら乾燥させた。
<Operation 2A>
An aluminum nitride dispersion having a mass of 0.5 g and an average particle size of D50 of 1.2 μm was added to the above-mentioned solution in which hexachloride platinum (IV) acid / hexahydrate was dissolved to prepare an aluminum nitride dispersion. The amount of the solution was adjusted so that the target loading amount of platinum was 1% by mass. A beaker containing the aluminum nitride dispersion was placed on a hot stirrer, and the aluminum nitride solution was dried while stirring with a stirring rod at a set temperature of 100 ° C.
 <操作3A>
 蒸発乾固後、実施例1の操作3の熱処理条件と同じ条件、同じ方法により、熱処理を行うことによって、実施例5の有機物分解用触媒を作製した。
<Operation 3A>
After evaporating to dryness, the catalyst for organic matter decomposition of Example 5 was prepared by performing heat treatment under the same conditions and the same method as the heat treatment conditions of Operation 3 of Example 1.
 <操作4A>
 作製した有機物分解用触媒を、実施例1の操作4の熱処理条件と同じ条件で熱処理した。
<Operation 4A>
The produced catalyst for decomposition of organic matter was heat-treated under the same conditions as the heat treatment conditions of operation 4 of Example 1.
 <操作5A>
 実施例1の操作5で説明した方法と同じ方法により、実施例5の有機物分解用触媒の表面の定性・半定量分析を行った。元素の定性・半定量分析結果を表4に示す。
<Operation 5A>
A qualitative and semi-quantitative analysis of the surface of the catalyst for organic matter decomposition of Example 5 was performed by the same method as that described in Operation 5 of Example 1. Table 4 shows the results of qualitative and semi-quantitative analysis of the elements.
Figure JPOXMLDOC01-appb-T000004
Figure JPOXMLDOC01-appb-T000004
 <操作6A>
 実施例1の操作6で説明した方法と同じ方法により、H2ガスの吸着量と、担体に担持させている白金ナノ粒子の分散度を求めた。また、H2ガスの吸着量から、800℃で熱処理を行う前後におけるH2ガスの単位吸着量と、白金質量あたりのH2ガス吸着量とを求めた。
<Operation 6A>
The amount of H 2 gas adsorbed and the degree of dispersion of platinum nanoparticles supported on the carrier were determined by the same method as described in step 6 of Example 1. Further, it determined from the adsorption amount of H 2 gas, and the unit amount of adsorption of H 2 gas before and after the heat treatment is performed at 800 ° C., and H 2 gas adsorption amount per platinum mass.
 (実施例6)
 白金の目標担持量が2質量%となるように調整したこと以外は、実施例5の有機物分解用触媒の作製方法と同じ方法により、実施例6の有機物分解用触媒を作製した。また、作製した有機物分解用触媒を、実施例1の操作4で説明した熱処理方法と同じ方法で熱処理した。
(Example 6)
The organic matter decomposition catalyst of Example 6 was prepared by the same method as the organic matter decomposition catalyst of Example 5 except that the target carrying amount of platinum was adjusted to be 2% by mass. Further, the produced catalyst for decomposition of organic matter was heat-treated by the same method as the heat treatment method described in operation 4 of Example 1.
 また、実施例1の操作6で説明した方法と同じ方法により、H2ガスの吸着量と白金ナノ粒子の分散度を求めた。H2ガスの吸着量から、800℃で熱処理を行う前後におけるH2ガスの単位吸着量と、白金質量あたりのH2ガス吸着量とを求めた。 In addition, the amount of H 2 gas adsorbed and the degree of dispersion of platinum nanoparticles were determined by the same method as described in step 6 of Example 1. From the adsorption amount of H 2 gas was determined and the unit amount of adsorption of H 2 gas before and after the heat treatment is performed at 800 ° C., and H 2 gas adsorption amount per platinum mass.
 また、実施例1の操作7で説明した方法と同じ方法により、実施例6の有機物分解用触媒の表面を観察した。実施例6の有機物分解用触媒の表面を観察したときの写真を図5に示す。 Further, the surface of the catalyst for organic matter decomposition of Example 6 was observed by the same method as that described in Operation 7 of Example 1. A photograph of the surface of the catalyst for decomposing organic matter of Example 6 is shown in FIG.
 また、実施例1の操作7で説明した方法と同じ方法により、担持されている白金ナノ粒子の平均粒径を求めた。 Further, the average particle size of the supported platinum nanoparticles was determined by the same method as that described in operation 7 of Example 1.
 (実施例7)
 白金の目標担持量が3質量%となるように調整したこと以外は、実施例5の有機物分解用触媒の作製方法と同じ方法により、実施例7の有機物分解用触媒を作製した。また、作製した有機物分解用触媒を、実施例1の操作4で説明した熱処理方法と同じ方法で熱処理した。
(Example 7)
The organic matter decomposition catalyst of Example 7 was prepared by the same method as the organic matter decomposition catalyst of Example 5 except that the target carrying amount of platinum was adjusted to 3% by mass. Further, the produced catalyst for decomposition of organic matter was heat-treated by the same method as the heat treatment method described in operation 4 of Example 1.
 また、実施例1の操作6で説明した方法と同じ方法により、H2ガスの吸着量と白金ナノ粒子の分散度を求めた。H2ガスの吸着量から、800℃で熱処理を行う前後におけるH2ガスの単位吸着量と、白金質量あたりのH2ガス吸着量とを求めた。 In addition, the amount of H 2 gas adsorbed and the degree of dispersion of platinum nanoparticles were determined by the same method as described in step 6 of Example 1. From the adsorption amount of H 2 gas was determined and the unit amount of adsorption of H 2 gas before and after the heat treatment is performed at 800 ° C., and H 2 gas adsorption amount per platinum mass.
 (実施例8)
 白金の目標担持量が5質量%となるように調整したこと以外は、実施例5の有機物分解用触媒の作製方法と同じ方法により、実施例8の有機物分解用触媒を作製した。また、作製した有機物分解用触媒を、実施例1の操作4で説明した熱処理方法と同じ方法で熱処理した。
(Example 8)
The organic matter decomposition catalyst of Example 8 was prepared by the same method as the method for producing the organic matter decomposition catalyst of Example 5 except that the target carrying amount of platinum was adjusted to 5% by mass. Further, the produced catalyst for decomposition of organic matter was heat-treated by the same method as the heat treatment method described in operation 4 of Example 1.
 また、実施例1の操作5で説明した方法と同じ方法により、実施例8の有機物分解用触媒の表面の定性・半定量分析を行った。元素の定性・半定量分析結果を表5に示す。 Further, qualitative and semi-quantitative analysis of the surface of the catalyst for organic matter decomposition of Example 8 was performed by the same method as that described in Operation 5 of Example 1. Table 5 shows the results of qualitative and semi-quantitative analysis of the elements.
Figure JPOXMLDOC01-appb-T000005
Figure JPOXMLDOC01-appb-T000005
 また、実施例1の操作6で説明した方法と同じ方法により、H2ガスの吸着量と白金ナノ粒子の分散度を求めた。H2ガスの吸着量から、800℃で熱処理を行う前後におけるH2ガスの単位吸着量と、白金質量あたりのH2ガス吸着量とを求めた。 In addition, the amount of H 2 gas adsorbed and the degree of dispersion of platinum nanoparticles were determined by the same method as described in step 6 of Example 1. From the adsorption amount of H 2 gas was determined and the unit amount of adsorption of H 2 gas before and after the heat treatment is performed at 800 ° C., and H 2 gas adsorption amount per platinum mass.
 以下で説明する比較例1~14の有機物分解用触媒は、上述した本発明の要件を満たしていない触媒である。 The catalysts for decomposition of organic substances of Comparative Examples 1 to 14 described below are catalysts that do not satisfy the above-mentioned requirements of the present invention.
 (比較例1)
 以下の操作1B~操作5Bの手順により、比較例1の有機物分解用触媒を作製した。
(Comparative Example 1)
The catalyst for decomposition of organic matter of Comparative Example 1 was prepared by the following procedures 1B to 5B.
 <操作1B>
 ヘキサクロリド白金(IV)酸・六水和物を超音波照射によって純水に溶解させ、白金の含有量が5質量%の溶液を作製した。
<Operation 1B>
Hexachloroplatin (IV) acid / hexahydrate was dissolved in pure water by ultrasonic irradiation to prepare a solution having a platinum content of 5% by mass.
 <操作2B>
 質量0.5g、平均粒径D50が1.2μmである窒化アルミニウム粉を上述したヘキサクロリド白金(IV)酸・六水和物が溶解した溶液に添加して、窒化アルミニウム分散液を作製した。そして、作製した窒化アルミニウム分散液を撹拌機によって300rpmで攪拌した。
<Operation 2B>
An aluminum nitride dispersion having a mass of 0.5 g and an average particle size of D50 of 1.2 μm was added to the above-mentioned solution in which hexachloride platinum (IV) acid / hexahydrate was dissolved to prepare an aluminum nitride dispersion. Then, the produced aluminum nitride dispersion was stirred with a stirrer at 300 rpm.
 その後、純水に溶解させて作製した0.1Mの水酸化ナトリウムを、上述した窒化アルミニウム分散液に50mL添加し、さらに、1Mの水酸化ナトリウム水溶液を10mL追加で添加した。pH調整のため、30分を要した後、リトマス試験紙を用いて窒化アルミニウム分散液のpHを調べると12であった。以後、pHが12となってから70℃で窒化アルミニウム分散液を攪拌した。攪拌中、45分経過した時点でのpHは11を示したため、pHを12に維持するために、1Mの水酸化ナトリウム水溶液を5mL追加した。以後、15分間で窒化アルミニウム分散液のpHは変化しなかった。 Then, 50 mL of 0.1 M sodium hydroxide prepared by dissolving in pure water was added to the above-mentioned aluminum nitride dispersion, and 10 mL of a 1 M sodium hydroxide aqueous solution was additionally added. After 30 minutes were required for pH adjustment, the pH of the aluminum nitride dispersion was examined using a Lithomas test paper and found to be 12. After that, the aluminum nitride dispersion was stirred at 70 ° C. after the pH reached 12. Since the pH was 11 after 45 minutes of stirring, 5 mL of 1 M aqueous sodium hydroxide solution was added to maintain the pH at 12. After that, the pH of the aluminum nitride dispersion did not change in 15 minutes.
 <操作3B>
 孔径1μmのメンブレンフィルタを用いて窒化アルミニウム分散液を固液分離させた。吸引濾過において、純水20mLを用いて3回行うことにより、メンブレンフィルタ表面に存在する粉体表面を洗浄した。
<Operation 3B>
The aluminum nitride dispersion was solid-liquid separated using a membrane filter having a pore size of 1 μm. The surface of the powder existing on the surface of the membrane filter was washed by performing suction filtration three times with 20 mL of pure water.
 <操作4B>
 スパチュラを用いてメンブレンフィルタから回収した粉体をアルミ製シャーレに入れ、真空低温乾燥機を用いて室温で一晩乾燥させた。
<Operation 4B>
The powder recovered from the membrane filter using a spatula was placed in an aluminum petri dish and dried overnight at room temperature using a vacuum low temperature dryer.
 <操作5B>
 上記操作4Bにより得られた乾燥物をアルミ製シャーレからるつぼに移し替え、500℃、1時間、大気下で熱処理した。その後、100℃以下の温度に低下させた熱処理炉内からるつぼを取り出した後、再度400℃、1時間、H2とN2の比(H2/N2)が3%である混合ガス流通下で熱処理することによって、比較例1の有機物分解用触媒を作製した。
<Operation 5B>
The dried product obtained by the above operation 4B was transferred from an aluminum petri dish to a crucible and heat-treated in the atmosphere at 500 ° C. for 1 hour. Then, after taking out the crucible from the heat treatment furnace whose temperature was lowered to 100 ° C. or lower, the mixed gas flow in which the ratio of H 2 to N 2 (H 2 / N 2) was 3% again at 400 ° C. for 1 hour. By heat-treating underneath, a catalyst for decomposition of organic matter of Comparative Example 1 was prepared.
 <操作6B>
 作製した有機物分解用触媒の表面を、日立製の走査型電子顕微鏡「HD-2300A」とEDAX製のエネルギー分散型X線分析装置「Genesis XM4」を用いて観察した。観察写真を図6に示す。有機物分解用触媒の表面を観察することにより、約5nmの大きさの白金ナノ粒子が窒化アルミニウムの表面に均一に担持されていることが確認できた。
<Operation 6B>
The surface of the produced catalyst for decomposition of organic matter was observed using a scanning electron microscope "HD-2300A" manufactured by Hitachi and an energy dispersive X-ray analyzer "Genesis XM4" manufactured by EDAX. The observation photograph is shown in FIG. By observing the surface of the catalyst for decomposition of organic matter, it was confirmed that platinum nanoparticles having a size of about 5 nm were uniformly supported on the surface of aluminum nitride.
 <操作7B>
 作製した有機物分解用触媒をるつぼに添加して、さらに800℃、2時間、大気下で熱処理した。
<Operation 7B>
The prepared catalyst for decomposition of organic matter was added to the crucible, and the mixture was further heat-treated at 800 ° C. for 2 hours in the atmosphere.
 <操作8B>
 るつぼ内から有機物分解用触媒を回収し、試料管に0.1g添加した。その後、有機物分解用触媒に対して、マイクロトラック・ベル社製の触媒分析装置「BELCAT」を用いて、400℃で水分などの吸着質を脱着して50℃まで冷却後、パルス化学吸着法により、H2ガスの吸着量と、担体に担持させている白金ナノ粒子の分散度を求めた。パルス化学吸着法では、キャリアガスとしてArを用い、濃度5体積%のH2ガスをパルス状に繰り返し導入した。導入したガスの流量は、30cm3/分、測定温度安定時間は15分である。
<Operation 8B>
The catalyst for decomposition of organic matter was recovered from the crucible, and 0.1 g was added to the sample tube. Then, the catalyst for decomposition of organic substances is desorbed from adsorbents such as water at 400 ° C. using a catalyst analyzer "BELCAT" manufactured by Microtrac Bell, cooled to 50 ° C., and then subjected to a pulse chemisorption method. , The amount of H 2 gas adsorbed and the degree of dispersion of platinum nanoparticles supported on the carrier were determined. In the pulse chemisorption method, Ar was used as the carrier gas, and H 2 gas having a concentration of 5% by volume was repeatedly introduced in a pulse shape. The flow rate of the introduced gas is 30 cm 3 / min, and the measurement temperature stabilization time is 15 minutes.
 H2ガスは、計量管内に120秒流し、10秒後に試料管に注入した。パルス検出の判断値は、0.001mV/秒とし、最終3パルスの検出器の差が1.2%以内で吸着平衡に至ったと判断した。これにより、H2ガスの吸着量と白金ナノ粒子の分散度を求めた。ここでも、操作7Cによる800℃での熱処理を行う前と、熱処理を行った後の両方において、H2ガスの吸着量を、有機物分解用触媒の質量で除算して得られる「H2ガスの単位吸着量」と、H2ガスの吸着量を、白金の質量で除算して得られる「白金質量あたりのH2ガス吸着量」とを求めた。 The H 2 gas was flowed into the measuring tube for 120 seconds and injected into the sample tube 10 seconds later. The judgment value of pulse detection was 0.001 mV / sec, and it was judged that the adsorption equilibrium was reached within 1.2% of the difference between the detectors of the final 3 pulses. As a result, the amount of H 2 gas adsorbed and the degree of dispersion of platinum nanoparticles were determined. Again, before performing the heat treatment at 800 ° C. due to the operation 7C, both after the heat treatment, the adsorption amount of H 2 gas, obtained by dividing by the mass of organic decomposition catalyst "of the H 2 gas a unit adsorption amount ", the amount of adsorption of H 2 gas were determined and obtained by dividing the mass of the platinum" H 2 gas adsorption amount per platinum mass ".
 (比較例2)
 以下の操作1C~操作5Cの手順により、比較例2の有機物分解用触媒を作製した。
(Comparative Example 2)
The catalyst for decomposition of organic matter of Comparative Example 2 was prepared by the following procedures 1C to 5C.
 <操作1C>
 ヘキサクロリド白金(IV)酸・六水和物を超音波照射によって純水に溶解させ、白金の含有量が0.58質量%、30mMの溶液を作製した。
<Operation 1C>
Hexachloroplatinic acid (IV) acid / hexahydrate was dissolved in pure water by ultrasonic irradiation to prepare a solution having a platinum content of 0.58% by mass and 30 mM.
 <操作2C>
 質量0.5g、平均粒径D50が1.2μmである窒化アルミニウム粉を超音波洗浄機で純水2mLに超音波分散させた後、上述したヘキサクロリド白金(IV)酸・六水和物が純水に溶解した溶液を4mL添加して、窒化アルミニウム分散液を作製した。溶液の添加量は、白金の目標担持量が5質量%となるように調整した。そして、窒化アルミニウム分散液を入れたビーカーをホットスターラー上に設置し、室温、500rpmで、窒化アルミニウム分散液を1時間攪拌した。
<Operation 2C>
After ultrasonically dispersing aluminum nitride powder having a mass of 0.5 g and an average particle size D50 of 1.2 μm in 2 mL of pure water with an ultrasonic cleaner, the above-mentioned hexachloride platinum (IV) acid / hexahydrate was obtained. An aluminum nitride dispersion was prepared by adding 4 mL of a solution dissolved in pure water. The amount of the solution added was adjusted so that the target loading amount of platinum was 5% by mass. Then, a beaker containing the aluminum nitride dispersion was placed on a hot stirrer, and the aluminum nitride dispersion was stirred at room temperature and 500 rpm for 1 hour.
 <操作3C>
 水酸化ホウ素ナトリウム0.85gを秤量し、N2バブリングを一晩行った純水9.15mLに溶解させて還元剤とした。還元剤の濃度は、85g/Lである。作製した還元剤を、マイクロピペットを用いて窒化アルミニウム分散液に緩慢に滴下した。還元剤の滴下により激しい発泡が生じ、黄色を呈した窒化アルミニウム分散液が一瞬で灰色に変化した。消泡後、2時間、窒化アルミニウム分散液を攪拌した。
<Operation 3C>
0.85 g of sodium borohydride was weighed and dissolved in 9.15 mL of pure water subjected to N 2 bubbling overnight to prepare a reducing agent. The concentration of the reducing agent is 85 g / L. The prepared reducing agent was slowly added dropwise to the aluminum nitride dispersion using a micropipette. The dropping of the reducing agent caused vigorous foaming, and the yellowish aluminum nitride dispersion instantly turned gray. After defoaming, the aluminum nitride dispersion was stirred for 2 hours.
 <操作4C>
 孔径1μmのメンブレンフィルタを用いて窒化アルミニウム分散液を固液分離させた。吸引濾過において、エタノール20mLを用いて3回行うことにより、メンブレンフィルタ表面に存在する粉体表面を洗浄した。
<Operation 4C>
The aluminum nitride dispersion was solid-liquid separated using a membrane filter having a pore size of 1 μm. The surface of the powder existing on the surface of the membrane filter was washed by performing suction filtration three times with 20 mL of ethanol.
 <操作5C>
 スパチュラを用いてメンブレンフィルタから回収した粉体をアルミ製シャーレに入れ、定温乾燥機を用いて、60℃、30分、大気下の条件で乾燥させることによって、比較例2の有機物分解用触媒を作製した。
<Operation 5C>
The powder recovered from the membrane filter using a spatula is placed in an aluminum petri dish and dried at 60 ° C. for 30 minutes under atmospheric conditions using a constant temperature dryer to obtain the catalyst for organic matter decomposition of Comparative Example 2. Made.
 <操作6C>
 比較例1の操作6Bで説明した方法と同じ方法により、作製した有機物分解用触媒の表面を観察した。観察写真を図7に示す。図7(a)は、観察倍率を10万倍としたときの写真であり、図7(b)は、観察倍率を60万倍としたときの写真である。有機物分解用触媒の表面を観察することにより、約15nmの大きさの白金ナノ粒子が窒化アルミニウムの表面に均一に担持されていることが確認できた。
<Operation 6C>
The surface of the produced catalyst for decomposition of organic matter was observed by the same method as that described in Operation 6B of Comparative Example 1. The observation photograph is shown in FIG. FIG. 7A is a photograph when the observation magnification is 100,000 times, and FIG. 7B is a photograph when the observation magnification is 600,000 times. By observing the surface of the catalyst for decomposition of organic matter, it was confirmed that platinum nanoparticles having a size of about 15 nm were uniformly supported on the surface of aluminum nitride.
 <操作7C>
 作製した有機物分解用触媒をるつぼに添加して、さらに800℃、2時間、大気下で熱処理した。
<Operation 7C>
The prepared catalyst for decomposition of organic matter was added to the crucible, and the mixture was further heat-treated at 800 ° C. for 2 hours in the atmosphere.
 <操作8C>
 比較例1の操作8Bで説明した方法と同じ方法により、H2ガスの吸着量と、担体に担持させている白金ナノ粒子の分散度を求めた。また、H2ガスの吸着量から、800℃で熱処理を行う前後におけるH2ガスの単位吸着量と、白金質量あたりのH2ガス吸着量とを求めた。
<Operation 8C>
The amount of H 2 gas adsorbed and the degree of dispersion of platinum nanoparticles supported on the carrier were determined by the same method as described in Operation 8B of Comparative Example 1. Further, it determined from the adsorption amount of H 2 gas, and the unit amount of adsorption of H 2 gas before and after the heat treatment is performed at 800 ° C., and H 2 gas adsorption amount per platinum mass.
 (比較例3)
 以下の操作1D~操作5Dの手順により、比較例3の有機物分解用触媒を作製した。
(Comparative Example 3)
The catalyst for organic matter decomposition of Comparative Example 3 was produced by the following procedures from Operation 1D to Operation 5D.
 <操作1D>
 比較例1の操作1Bと同様に、ヘキサクロリド白金(IV)酸・六水和物を超音波照射によって純水に溶解させて、白金の含有量が5質量%の溶液を作製した。
<Operation 1D>
In the same manner as in Operation 1B of Comparative Example 1, hexachloride platinum (IV) acid / hexahydrate was dissolved in pure water by ultrasonic irradiation to prepare a solution having a platinum content of 5% by mass.
 <操作2D>
 ヘキサクロリド白金(IV)酸・六水和物が溶解した溶液に対して、1Mの水酸化ナトリウム水溶液を1.3mL添加した。この溶液のpHを、堀場製作所製のpHメータを用いて測定したところ、12.43であった。
<Operation 2D>
1.3 mL of 1 M aqueous sodium hydroxide solution was added to the solution in which hexachloride platinum (IV) acid / hexahydrate was dissolved. The pH of this solution was measured using a pH meter manufactured by HORIBA, Ltd. and found to be 12.43.
 続いて、質量1g、平均粒径D50が1.2μmである窒化アルミニウム粉を、上述したpH調整を行った溶液に添加することによって、窒化アルミニウム分散液を作製した。そして、窒化アルミニウム分散液を入れたビーカーをホットスターラー上に設置し、設定温度を100℃として、窒化アルミニウム分散液を攪拌棒で攪拌しながら乾燥させた。 Subsequently, an aluminum nitride dispersion having a mass of 1 g and an average particle size of D50 of 1.2 μm was added to the above-mentioned pH-adjusted solution to prepare an aluminum nitride dispersion. Then, a beaker containing the aluminum nitride dispersion was placed on a hot stirrer, and the aluminum nitride dispersion was dried while stirring with a stirring rod at a set temperature of 100 ° C.
 <操作3D>
 比較例1の操作3Bで説明した洗浄方法と同じ方法により、窒化アルミニウム分散液を固液分離させた後、メンブレンフィルタ表面に存在する粉体表面を洗浄した。
<Operation 3D>
The aluminum nitride dispersion was solid-liquid separated by the same cleaning method as that described in Operation 3B of Comparative Example 1, and then the powder surface existing on the membrane filter surface was cleaned.
 <操作4D>
 比較例1の操作4Bで説明した乾燥方法と同じ方法により、粉体を乾燥させた。
<Operation 4D>
The powder was dried by the same method as the drying method described in Operation 4B of Comparative Example 1.
 <操作5D>
 比較例1の操作5Bで説明した熱処理方法と同じ方法によって、乾燥物を熱処理することにより、比較例3の有機物分解用触媒を作製した。
<Operation 5D>
The organic matter decomposition catalyst of Comparative Example 3 was prepared by heat-treating the dried product by the same method as the heat treatment method described in Operation 5B of Comparative Example 1.
 <操作6D>
 比較例1の操作6Bで説明した方法と同じ方法により、作製した有機物分解用触媒の表面を観察した。観察写真を図8に示す。図8(a)は、観察倍率を15万倍としたときの写真であり、図8(b)は、観察倍率を60万倍としたときの写真である。有機物分解用触媒の表面を観察することにより、約25nmの大きさの白金ナノ粒子が窒化アルミニウムの表面に均一に担持されていることが確認できた。
<Operation 6D>
The surface of the produced catalyst for decomposition of organic matter was observed by the same method as that described in Operation 6B of Comparative Example 1. The observation photograph is shown in FIG. FIG. 8A is a photograph when the observation magnification is 150,000 times, and FIG. 8B is a photograph when the observation magnification is 600,000 times. By observing the surface of the catalyst for decomposition of organic matter, it was confirmed that platinum nanoparticles having a size of about 25 nm were uniformly supported on the surface of aluminum nitride.
 <操作7D>
 比較例1の操作7Bで説明した熱処理方法と同じ方法によって、有機物分解用触媒に対して熱処理を行った。
<Operation 7D>
The organic matter decomposition catalyst was heat-treated by the same method as the heat treatment method described in operation 7B of Comparative Example 1.
 <操作8D>
 比較例1の操作8Bで説明した方法と同じ方法により、H2ガスの吸着量と、担体に担持させている白金ナノ粒子の分散度を求めた。また、H2ガスの吸着量から、800℃で熱処理を行う前後におけるH2ガスの単位吸着量と、白金質量あたりのH2ガス吸着量とを求めた。
<Operation 8D>
The amount of H 2 gas adsorbed and the degree of dispersion of platinum nanoparticles supported on the carrier were determined by the same method as described in Operation 8B of Comparative Example 1. Further, it determined from the adsorption amount of H 2 gas, and the unit amount of adsorption of H 2 gas before and after the heat treatment is performed at 800 ° C., and H 2 gas adsorption amount per platinum mass.
 (比較例4)
 以下の操作1E~操作5Eの手順により、比較例4の有機物分解用触媒を作製した。
(Comparative Example 4)
The catalyst for decomposition of organic matter of Comparative Example 4 was prepared by the following procedures from Operation 1E to Operation 5E.
 <操作1E>
 比較例1の操作1Bと同様に、ヘキサクロリド白金(IV)酸・六水和物を超音波照射によって純水に溶解させ、白金の含有量が5質量%の溶液を作製した。
<Operation 1E>
In the same manner as in Operation 1B of Comparative Example 1, hexachloride platinum (IV) acid / hexahydrate was dissolved in pure water by ultrasonic irradiation to prepare a solution having a platinum content of 5% by mass.
 <操作2E>
 ヘキサクロリド白金(IV)酸・六水和物が溶解した溶液に対して、1Mの水酸化ナトリウム水溶液を1.23mL添加した。この溶液のpHを、堀場製作所製のpHメータを用いて測定したところ、7.09であった。
<Operation 2E>
1.23 mL of 1 M aqueous sodium hydroxide solution was added to the solution in which hexachloride platinum (IV) acid / hexahydrate was dissolved. The pH of this solution was measured using a pH meter manufactured by HORIBA, Ltd. and found to be 7.09.
 続いて、質量1g、平均粒径D50が1.2μmである窒化アルミニウム粉を、上述したpH調整を行った溶液に添加することにより、窒化アルミニウム分散液を作製した。そして、窒化アルミニウム分散液を入れたビーカーをホットスターラー上に設置し、設定温度を100℃として、窒化アルミニウム分散液を攪拌棒で攪拌しながら乾燥させた。 Subsequently, an aluminum nitride dispersion having a mass of 1 g and an average particle size of D50 of 1.2 μm was added to the above-mentioned pH-adjusted solution to prepare an aluminum nitride dispersion. Then, a beaker containing the aluminum nitride dispersion was placed on a hot stirrer, and the aluminum nitride dispersion was dried while stirring with a stirring rod at a set temperature of 100 ° C.
 <操作3E>
 比較例1の操作3Bで説明した洗浄方法と同じ方法により、窒化アルミニウム分散液を固液分離させた後、メンブレンフィルタ表面に存在する粉体表面を洗浄した。
<Operation 3E>
The aluminum nitride dispersion was solid-liquid separated by the same cleaning method as that described in Operation 3B of Comparative Example 1, and then the powder surface existing on the membrane filter surface was cleaned.
 <操作4E>
 スパチュラを用いてメンブレンフィルタから回収した粉体をアルミ製シャーレに入れ、定温乾燥機を用いて、110℃、3時間、大気下の条件で乾燥させた。
<Operation 4E>
The powder recovered from the membrane filter using a spatula was placed in an aluminum petri dish and dried at 110 ° C. for 3 hours under atmospheric conditions using a constant temperature dryer.
 <操作5E>
 比較例1の操作5Bで説明した熱処理方法と同じ方法によって、乾燥物を熱処理することにより、比較例4の有機物分解用触媒を作製した。
<Operation 5E>
The organic matter decomposition catalyst of Comparative Example 4 was prepared by heat-treating the dried product by the same method as the heat treatment method described in Operation 5B of Comparative Example 1.
 <操作6E>
 比較例1の操作6Bで説明した方法と同じ方法により、作製した有機物分解用触媒の表面を観察した。観察写真を図9に示す。有機物分解用触媒の表面を観察することにより、約50nmの大きさの白金ナノ粒子が窒化アルミニウムの表面に均一に担持されていることが確認できた。
<Operation 6E>
The surface of the produced catalyst for decomposition of organic matter was observed by the same method as that described in Operation 6B of Comparative Example 1. The observation photograph is shown in FIG. By observing the surface of the catalyst for decomposition of organic matter, it was confirmed that platinum nanoparticles having a size of about 50 nm were uniformly supported on the surface of aluminum nitride.
 <操作7E>
 比較例1の操作7Bで説明した熱処理方法と同じ方法によって、有機物分解用触媒に対して熱処理を行った。
<Operation 7E>
The organic matter decomposition catalyst was heat-treated by the same method as the heat treatment method described in operation 7B of Comparative Example 1.
 <操作8E>
 比較例1の操作8Bで説明した方法と同じ方法により、H2ガスの吸着量と、担体に担持させている白金ナノ粒子の分散度を求めた。また、H2ガスの吸着量から、800℃で熱処理を行う前後におけるH2ガスの単位吸着量と、白金質量あたりのH2ガス吸着量とを求めた。
<Operation 8E>
The amount of H 2 gas adsorbed and the degree of dispersion of platinum nanoparticles supported on the carrier were determined by the same method as described in Operation 8B of Comparative Example 1. Further, it determined from the adsorption amount of H 2 gas, and the unit amount of adsorption of H 2 gas before and after the heat treatment is performed at 800 ° C., and H 2 gas adsorption amount per platinum mass.
 (比較例5)
 以下の操作1F~操作5Fの手順により、比較例5の有機物分解用触媒を作製した。
(Comparative Example 5)
The catalyst for organic matter decomposition of Comparative Example 5 was produced by the following procedures from Operation 1F to Operation 5F.
 <操作1F>
 比較例1の操作1Bと同様に、ヘキサクロリド白金(IV)酸・六水和物を超音波照射によって純水に溶解させ、白金の含有量が5質量%の溶液を作製した。
<Operation 1F>
In the same manner as in Operation 1B of Comparative Example 1, hexachloride platinum (IV) acid / hexahydrate was dissolved in pure water by ultrasonic irradiation to prepare a solution having a platinum content of 5% by mass.
 <操作2F>
 ヘキサクロリド白金(IV)酸・六水和物が溶解した溶液に対して、1Mの水酸化ナトリウム水溶液を1.30mL添加した。この溶液のpHを、堀場製作所製のpHメータを用いて測定したところ、12.43であった。
<Operation 2F>
1.30 mL of a 1 M aqueous sodium hydroxide solution was added to a solution in which hexachloride platinum (IV) acid / hexahydrate was dissolved. The pH of this solution was measured using a pH meter manufactured by HORIBA, Ltd. and found to be 12.43.
 続いて、質量1g、平均粒径D50が1.2μmである窒化アルミニウム粉を、上述したpH調整を行った溶液に添加することにより、窒化アルミニウム分散液を作製した。そして、窒化アルミニウム分散液を入れたビーカーをホットスターラー上に設置し、設定温度を100℃として、窒化アルミニウム分散液を攪拌棒で攪拌しながら乾燥させた。 Subsequently, an aluminum nitride dispersion having a mass of 1 g and an average particle size of D50 of 1.2 μm was added to the above-mentioned pH-adjusted solution to prepare an aluminum nitride dispersion. Then, a beaker containing the aluminum nitride dispersion was placed on a hot stirrer, and the aluminum nitride dispersion was dried while stirring with a stirring rod at a set temperature of 100 ° C.
 <操作3F>
 比較例1の操作3Bで説明した洗浄方法と同じ方法により、窒化アルミニウム分散液を固液分離させた後、メンブレンフィルタ表面に存在する粉体表面を洗浄した。
<Operation 3F>
The aluminum nitride dispersion was solid-liquid separated by the same cleaning method as that described in Operation 3B of Comparative Example 1, and then the powder surface existing on the membrane filter surface was cleaned.
 <操作4F>
 比較例1の操作4Bで説明した乾燥方法と同じ方法により、粉体を乾燥させた。
<Operation 4F>
The powder was dried by the same method as the drying method described in Operation 4B of Comparative Example 1.
 <操作5F>
 比較例1の操作5Bで説明した熱処理方法と同じ方法によって、乾燥物を熱処理することにより、比較例5の有機物分解用触媒を作製した。
<Operation 5F>
The organic matter decomposition catalyst of Comparative Example 5 was prepared by heat-treating the dried product by the same method as the heat treatment method described in Operation 5B of Comparative Example 1.
 <操作6F>
 比較例1の操作6Bで説明した方法と同じ方法により、作製した有機物分解用触媒の表面を観察した。観察写真を図10に示す。有機物分解用触媒の表面を観察することにより、約60nmの大きさの白金ナノ粒子が窒化アルミニウムの表面に均一に担持されていることが確認できた。
<Operation 6F>
The surface of the produced catalyst for decomposition of organic matter was observed by the same method as that described in Operation 6B of Comparative Example 1. The observation photograph is shown in FIG. By observing the surface of the catalyst for decomposition of organic matter, it was confirmed that platinum nanoparticles having a size of about 60 nm were uniformly supported on the surface of aluminum nitride.
 <操作7F>
 比較例1の操作7Bで説明した熱処理方法と同じ方法によって、有機物分解用触媒に対して熱処理を行った。
<Operation 7F>
The organic matter decomposition catalyst was heat-treated by the same method as the heat treatment method described in operation 7B of Comparative Example 1.
 <操作8F>
 比較例1の操作8Bで説明した方法と同じ方法により、H2ガスの吸着量と、担体に担持させている白金ナノ粒子の分散度を求めた。また、H2ガスの吸着量から、800℃で熱処理を行う前後におけるH2ガスの単位吸着量と、白金質量あたりのH2ガス吸着量とを求めた。
<Operation 8F>
The amount of H 2 gas adsorbed and the degree of dispersion of platinum nanoparticles supported on the carrier were determined by the same method as described in Operation 8B of Comparative Example 1. Further, it determined from the adsorption amount of H 2 gas, and the unit amount of adsorption of H 2 gas before and after the heat treatment is performed at 800 ° C., and H 2 gas adsorption amount per platinum mass.
 (比較例6)
 以下の操作1G~操作3Gの手順により、比較例6の有機物分解用触媒を作製した。
(Comparative Example 6)
The catalyst for organic matter decomposition of Comparative Example 6 was produced by the following procedures from Operation 1G to Operation 3G.
 <操作1G>
 ヘキサクロリド白金(IV)酸・六水和物を超音波照射によって純水に溶解させ、白金の含有量が1質量%の溶液を作製した。
<Operation 1G>
Hexachloroplatinic acid (IV) acid / hexahydrate was dissolved in pure water by ultrasonic irradiation to prepare a solution having a platinum content of 1% by mass.
 <操作2G>
 上述したヘキサクロリド白金(IV)酸・六水和物が溶解した溶液に、粒径2~3μm程度で、0.5gのα-アルミナ粉を添加して、α-アルミナ分散液を作製した。溶液の量は、白金の目標担持量が1質量%となるように調整した。そして、α-アルミナ分散液を入れたビーカーをホットスターラー上に設置し、設定温度100℃で、α-アルミナ分散液を攪拌棒で攪拌しながら乾燥させた。
<Operation 2G>
An α-alumina dispersion was prepared by adding 0.5 g of α-alumina powder having a particle size of about 2 to 3 μm to the solution in which the above-mentioned hexachloride platinum (IV) acid / hexahydrate was dissolved. The amount of the solution was adjusted so that the target loading amount of platinum was 1% by mass. Then, a beaker containing the α-alumina dispersion was placed on a hot stirrer, and the α-alumina dispersion was dried while stirring with a stirring rod at a set temperature of 100 ° C.
 <操作3G>
 蒸発乾固後、比較例1の操作5Bで説明した熱処理方法と同じ方法で熱処理を行うことにより、比較例6の有機物分解用触媒を作製した。
<Operation 3G>
After evaporating to dryness, the catalyst for organic matter decomposition of Comparative Example 6 was produced by performing heat treatment in the same manner as the heat treatment method described in Operation 5B of Comparative Example 1.
 <操作4G>
 作製した有機物分解用触媒を、比較例1の操作7Bで説明した熱処理方法と同じ方法によって、熱処理を行った。
<Operation 4G>
The produced catalyst for decomposition of organic matter was heat-treated by the same method as the heat treatment method described in operation 7B of Comparative Example 1.
 <操作5G>
 比較例1の操作8Bで説明した方法と同じ方法により、H2ガスの吸着量と、担体に担持させている白金ナノ粒子の分散度を求めた。また、H2ガスの吸着量から、800℃で熱処理を行う前後におけるH2ガスの単位吸着量と、白金質量あたりのH2ガス吸着量とを求めた。
<Operation 5G>
The amount of H 2 gas adsorbed and the degree of dispersion of platinum nanoparticles supported on the carrier were determined by the same method as described in Operation 8B of Comparative Example 1. Further, it determined from the adsorption amount of H 2 gas, and the unit amount of adsorption of H 2 gas before and after the heat treatment is performed at 800 ° C., and H 2 gas adsorption amount per platinum mass.
 (比較例7)
 白金の目標担持量が2質量%となるように調整したこと以外は、比較例6の有機物分解用触媒の作製方法と同じ方法により、比較例7の有機物分解用触媒を作製した。また、作製した有機物分解用触媒を、比較例1の操作7Bで説明した熱処理方法と同じ方法で熱処理した。
(Comparative Example 7)
The organic matter decomposition catalyst of Comparative Example 7 was prepared by the same method as the method for producing the organic matter decomposition catalyst of Comparative Example 6 except that the target carrying amount of platinum was adjusted to be 2% by mass. Further, the produced catalyst for decomposition of organic matter was heat-treated by the same method as the heat treatment method described in operation 7B of Comparative Example 1.
 実施例1の操作7で説明した方法と同じ方法により、比較例7の有機物分解用触媒の表面を観察した。比較例7の有機物分解用触媒の表面を観察したときの写真を図11に示す。 The surface of the catalyst for organic matter decomposition of Comparative Example 7 was observed by the same method as that described in Operation 7 of Example 1. FIG. 11 shows a photograph of Comparative Example 7 when the surface of the catalyst for decomposition of organic matter was observed.
 比較例1の操作8Bで説明した方法と同じ方法により、H2ガスの吸着量と、担体に担持させている白金ナノ粒子の分散度を求めた。また、H2ガスの吸着量から、800℃で熱処理を行う前後におけるH2ガスの単位吸着量と、白金質量あたりのH2ガス吸着量とを求めた。 The amount of H 2 gas adsorbed and the degree of dispersion of platinum nanoparticles supported on the carrier were determined by the same method as described in Operation 8B of Comparative Example 1. Further, it determined from the adsorption amount of H 2 gas, and the unit amount of adsorption of H 2 gas before and after the heat treatment is performed at 800 ° C., and H 2 gas adsorption amount per platinum mass.
 また、実施例1の操作7で説明した方法と同じ方法により、担持されている白金ナノ粒子の平均粒径を求めた。 Further, the average particle size of the supported platinum nanoparticles was determined by the same method as that described in operation 7 of Example 1.
 (比較例8)
 白金の目標担持量が3質量%となるように調整したこと以外は、比較例6の有機物分解用触媒の作製方法と同じ方法により、比較例8の有機物分解用触媒を作製した。また、作製した有機物分解用触媒を、比較例1の操作7Bで説明した熱処理方法と同じ方法で熱処理した。
(Comparative Example 8)
The organic matter decomposition catalyst of Comparative Example 8 was prepared by the same method as the method for producing the organic matter decomposition catalyst of Comparative Example 6 except that the target carrying amount of platinum was adjusted to 3% by mass. Further, the produced catalyst for decomposition of organic matter was heat-treated by the same method as the heat treatment method described in operation 7B of Comparative Example 1.
 比較例1の操作8Bで説明した方法と同じ方法により、H2ガスの吸着量と、担体に担持させている白金ナノ粒子の分散度を求めた。また、H2ガスの吸着量から、800℃で熱処理を行う前後におけるH2ガスの単位吸着量と、白金質量あたりのH2ガス吸着量とを求めた。 The amount of H 2 gas adsorbed and the degree of dispersion of platinum nanoparticles supported on the carrier were determined by the same method as described in Operation 8B of Comparative Example 1. Further, it determined from the adsorption amount of H 2 gas, and the unit amount of adsorption of H 2 gas before and after the heat treatment is performed at 800 ° C., and H 2 gas adsorption amount per platinum mass.
 (比較例9)
 白金の目標担持量が5質量%となるように調整したこと以外は、比較例6の有機物分解用触媒の作製方法と同じ方法により、比較例9の有機物分解用触媒を作製した。また、作製した有機物分解用触媒を、比較例1の操作7Bで説明した熱処理方法と同じ方法で熱処理した。
(Comparative Example 9)
The organic matter decomposition catalyst of Comparative Example 9 was prepared by the same method as the method for producing the organic matter decomposition catalyst of Comparative Example 6 except that the target carrying amount of platinum was adjusted to 5% by mass. Further, the produced catalyst for decomposition of organic matter was heat-treated by the same method as the heat treatment method described in operation 7B of Comparative Example 1.
 比較例1の操作8Bで説明した方法と同じ方法により、H2ガスの吸着量と、担体に担持させている白金ナノ粒子の分散度を求めた。また、H2ガスの吸着量から、800℃で熱処理を行う前後におけるH2ガスの単位吸着量と、白金質量あたりのH2ガス吸着量とを求めた。 The amount of H 2 gas adsorbed and the degree of dispersion of platinum nanoparticles supported on the carrier were determined by the same method as described in Operation 8B of Comparative Example 1. Further, it determined from the adsorption amount of H 2 gas, and the unit amount of adsorption of H 2 gas before and after the heat treatment is performed at 800 ° C., and H 2 gas adsorption amount per platinum mass.
 (比較例10)
 以下の操作1H~操作3Hの手順により、比較例10の有機物分解用触媒を作製した。なお、比較例10の有機物分解用触媒は、特開2003-144933号公報に記載の実施例19の触媒に相当するものである。
(Comparative Example 10)
The catalyst for organic matter decomposition of Comparative Example 10 was prepared by the following procedures from Operation 1H to Operation 3H. The catalyst for decomposition of organic matter in Comparative Example 10 corresponds to the catalyst of Example 19 described in JP-A-2003-144933.
 <操作1H>
 ヘキサクロリド白金(IV)酸・六水和物を超音波照射によって純水に溶解させ、白金の含有量が0.58質量%で30mMの溶液を作製した。
<Operation 1H>
Hexachloroplatinic acid (IV) acid / hexahydrate was dissolved in pure water by ultrasonic irradiation to prepare a solution having a platinum content of 0.58% by mass and 30 mM.
 <操作2H>
 平均粒径D50が1.2μmである窒化アルミニウム粉を、1000℃、2時間、大気下の条件で熱処理した。熱処理された窒化アルミニウム粉0.5gを、上述したヘキサクロリド白金(IV)酸・六水和物が溶解した溶液に添加して、窒化アルミニウム分散液を作製した。溶液の量は、白金の目標担持量が0.5質量%となるように調整した。窒化アルミニウム分散液を入れたビーカーを、ホットスターラー上に設置し、設定温度100℃で、窒化アルミニウム分散液を攪拌棒で攪拌しながら乾燥させた。
<Operation 2H>
Aluminum nitride powder having an average particle size D50 of 1.2 μm was heat-treated at 1000 ° C. for 2 hours under atmospheric conditions. 0.5 g of the heat-treated aluminum nitride powder was added to the above-mentioned solution in which the hexachloride platinum (IV) acid / hexahydrate was dissolved to prepare an aluminum nitride dispersion. The amount of the solution was adjusted so that the target loading amount of platinum was 0.5% by mass. A beaker containing the aluminum nitride dispersion was placed on a hot stirrer, and the aluminum nitride dispersion was dried while stirring with a stirring rod at a set temperature of 100 ° C.
 <操作3H>
 蒸発乾固後、比較例1の操作5Bで説明した熱処理方法と同じ方法で熱処理を行うことにより、比較例10の有機物分解用触媒を作製した。
<Operation 3H>
After evaporating to dryness, a catalyst for decomposition of organic substances of Comparative Example 10 was prepared by performing a heat treatment in the same manner as the heat treatment method described in Operation 5B of Comparative Example 1.
 <操作4H>
 実施例1の操作5で説明した方法と同じ方法により、比較例10の有機物分解用触媒の表面の定性・半定量分析を行った。元素の定性・半定量分析結果を表6に示す。
<Operation 4H>
A qualitative and semi-quantitative analysis of the surface of the catalyst for organic matter decomposition of Comparative Example 10 was performed by the same method as that described in Operation 5 of Example 1. Table 6 shows the results of qualitative and semi-quantitative analysis of the elements.
Figure JPOXMLDOC01-appb-T000006
Figure JPOXMLDOC01-appb-T000006
 <操作5H>
 比較例1の操作7Bで説明した熱処理方法と同じ方法によって、熱処理を行った。
<Operation 5H>
The heat treatment was performed by the same method as the heat treatment method described in the operation 7B of Comparative Example 1.
 <操作6H>
 比較例1の操作8Bで説明した方法と同じ方法により、H2ガスの吸着量と、担体に担持させている白金ナノ粒子の分散度を求めた。また、H2ガスの吸着量から、800℃で熱処理を行う前後におけるH2ガスの単位吸着量と、白金質量あたりのH2ガス吸着量とを求めた。
<Operation 6H>
The amount of H 2 gas adsorbed and the degree of dispersion of platinum nanoparticles supported on the carrier were determined by the same method as described in Operation 8B of Comparative Example 1. Further, it determined from the adsorption amount of H 2 gas, and the unit amount of adsorption of H 2 gas before and after the heat treatment is performed at 800 ° C., and H 2 gas adsorption amount per platinum mass.
 (比較例11)
 白金の目標担持量が1質量%となるように調整したこと以外は、比較例10の有機物分解用触媒の作製方法と同じ方法により、比較例11の有機物分解用触媒を作製した。また、作製した有機物分解用触媒を、比較例1の操作7Bで説明した熱処理方法と同じ方法で熱処理した。
(Comparative Example 11)
The organic matter decomposition catalyst of Comparative Example 11 was prepared by the same method as the method for producing the organic matter decomposition catalyst of Comparative Example 10 except that the target carrying amount of platinum was adjusted to 1% by mass. Further, the produced catalyst for decomposition of organic matter was heat-treated by the same method as the heat treatment method described in operation 7B of Comparative Example 1.
 比較例1の操作8Bで説明した方法と同じ方法により、H2ガスの吸着量と、担体に担持させている白金ナノ粒子の分散度を求めた。また、H2ガスの吸着量から、800℃で熱処理を行う前後におけるH2ガスの単位吸着量と、白金質量あたりのH2ガス吸着量とを求めた。 The amount of H 2 gas adsorbed and the degree of dispersion of platinum nanoparticles supported on the carrier were determined by the same method as described in Operation 8B of Comparative Example 1. Further, it determined from the adsorption amount of H 2 gas, and the unit amount of adsorption of H 2 gas before and after the heat treatment is performed at 800 ° C., and H 2 gas adsorption amount per platinum mass.
 (比較例12)
 白金の目標担持量が2質量%となるように調整したこと以外は、比較例10の有機物分解用触媒の作製方法と同じ方法により、比較例12の有機物分解用触媒を作製した。また、作製した有機物分解用触媒を、比較例1の操作7Bで説明した熱処理方法と同じ方法で熱処理した。
(Comparative Example 12)
The organic matter decomposition catalyst of Comparative Example 12 was prepared by the same method as the method for producing the organic matter decomposition catalyst of Comparative Example 10 except that the target carrying amount of platinum was adjusted to be 2% by mass. Further, the produced catalyst for decomposition of organic matter was heat-treated by the same method as the heat treatment method described in operation 7B of Comparative Example 1.
 比較例1の操作8Bで説明した方法と同じ方法により、H2ガスの吸着量と、担体に担持させている白金ナノ粒子の分散度を求めた。また、H2ガスの吸着量から、800℃で熱処理を行う前後におけるH2ガスの単位吸着量と、白金質量あたりのH2ガス吸着量とを求めた。 The amount of H 2 gas adsorbed and the degree of dispersion of platinum nanoparticles supported on the carrier were determined by the same method as described in Operation 8B of Comparative Example 1. Further, it determined from the adsorption amount of H 2 gas, and the unit amount of adsorption of H 2 gas before and after the heat treatment is performed at 800 ° C., and H 2 gas adsorption amount per platinum mass.
 (比較例13)
 白金の目標担持量が3質量%となるように調整したこと以外は、比較例10の有機物分解用触媒の作製方法と同じ方法により、比較例13の有機物分解用触媒を作製した。また、作製した有機物分解用触媒を、比較例1の操作7Bで説明した熱処理方法と同じ方法で熱処理した。
(Comparative Example 13)
The organic matter decomposition catalyst of Comparative Example 13 was prepared by the same method as the method for producing the organic matter decomposition catalyst of Comparative Example 10 except that the target carrying amount of platinum was adjusted to be 3% by mass. Further, the produced catalyst for decomposition of organic matter was heat-treated by the same method as the heat treatment method described in operation 7B of Comparative Example 1.
 比較例1の操作8Bで説明した方法と同じ方法により、H2ガスの吸着量と、担体に担持させている白金ナノ粒子の分散度を求めた。また、H2ガスの吸着量から、800℃で熱処理を行う前後におけるH2ガスの単位吸着量と、白金質量あたりのH2ガス吸着量とを求めた。 The amount of H 2 gas adsorbed and the degree of dispersion of platinum nanoparticles supported on the carrier were determined by the same method as described in Operation 8B of Comparative Example 1. Further, it determined from the adsorption amount of H 2 gas, and the unit amount of adsorption of H 2 gas before and after the heat treatment is performed at 800 ° C., and H 2 gas adsorption amount per platinum mass.
 (比較例14)
 白金の目標担持量が5質量%となるように調整したこと以外は、比較例10の有機物分解用触媒の作製方法と同じ方法により、比較例14の有機物分解用触媒を作製した。また、作製した有機物分解用触媒を、比較例1の操作7Bで説明した熱処理方法と同じ方法で熱処理した。なお、比較例14の有機物分解用触媒は、特開2003-144933号公報に記載の実施例20の触媒に相当するものである。
(Comparative Example 14)
The organic matter decomposition catalyst of Comparative Example 14 was prepared by the same method as the method for producing the organic matter decomposition catalyst of Comparative Example 10 except that the target carrying amount of platinum was adjusted to 5% by mass. Further, the produced catalyst for decomposition of organic matter was heat-treated by the same method as the heat treatment method described in operation 7B of Comparative Example 1. The catalyst for decomposition of organic matter of Comparative Example 14 corresponds to the catalyst of Example 20 described in JP-A-2003-144933.
 実施例1の操作5で説明した方法と同じ方法により、比較例14の有機物分解用触媒の表面の定性・半定量分析を行った。元素の定性・半定量分析結果を表7に示す。 The surface of the catalyst for organic matter decomposition of Comparative Example 14 was qualitatively and semi-quantitatively analyzed by the same method as that described in Operation 5 of Example 1. Table 7 shows the results of qualitative and semi-quantitative analysis of the elements.
Figure JPOXMLDOC01-appb-T000007
Figure JPOXMLDOC01-appb-T000007
 比較例1の操作8Bで説明した方法と同じ方法により、H2ガスの吸着量と、担体に担持させている白金ナノ粒子の分散度を求めた。また、H2ガスの吸着量から、800℃で熱処理を行う前後におけるH2ガスの単位吸着量と、白金質量あたりのH2ガス吸着量とを求めた。 The amount of H 2 gas adsorbed and the degree of dispersion of platinum nanoparticles supported on the carrier were determined by the same method as described in Operation 8B of Comparative Example 1. Further, it determined from the adsorption amount of H 2 gas, and the unit amount of adsorption of H 2 gas before and after the heat treatment is performed at 800 ° C., and H 2 gas adsorption amount per platinum mass.
 ここで、実施例1、4、5、8と比較例10、14の有機物分解用触媒の表面の定性・半定量分析結果と、表面に存在するNとAlの原子%比N/Alを表8に示す。 Here, the qualitative / semi-quantitative analysis results of the surfaces of the catalysts for organic matter decomposition of Examples 1, 4, 5 and 8 and Comparative Examples 10 and 14 and the atomic% ratio N / Al of N and Al existing on the surface are shown. Shown in 8.
Figure JPOXMLDOC01-appb-T000008
Figure JPOXMLDOC01-appb-T000008
 表8に示すように、実施例1、4、5、8の有機物分解用触媒の担体の表面に存在するNとAlの原子%比N/Alは、0.40以上0.50以下である。なお、表8には示していないが、実施例2、3、6、7の有機物分解用触媒の担体の表面に存在するNとAlの原子%比N/Alが0.40以上0.50以下であることも確認できた。また、比較例10および14の有機物分解用触媒だけでなく、比較例1~9および11~13の有機物分解用触媒の担体の表面に存在するNとAlの原子%比N/Alが0.40以上0.50以下の範囲外であることも確認できた。 As shown in Table 8, the atomic% ratio N / Al of N and Al present on the surface of the carrier of the catalyst for organic matter decomposition of Examples 1, 4, 5, and 8 is 0.40 or more and 0.50 or less. .. Although not shown in Table 8, the atomic% ratio N / Al of N and Al present on the surface of the carrier of the catalyst for organic matter decomposition of Examples 2, 3, 6 and 7 is 0.40 or more and 0.50. It was also confirmed that it was as follows. Further, not only the organic matter decomposition catalysts of Comparative Examples 10 and 14 but also the atomic% ratio N / Al of N and Al present on the surface of the carrier of the organic matter decomposition catalysts of Comparative Examples 1 to 9 and 11 to 13 was 0. It was also confirmed that it was out of the range of 40 or more and 0.50 or less.
 上述した実施例1~8および比較例1~14の有機物分解用触媒について、白金の目標担持量、800℃の熱処理後におけるH2ガス単位吸着量と白金質量あたりのH2ガス吸着量、熱処理前におけるH2ガス単位吸着量と白金質量あたりのH2ガス吸着量、および、800℃の熱処理による白金質量あたりのH2ガス吸着量の低下率を表9に示す。熱処理による白金質量あたりのH2ガス吸着量の低下率Rは、熱処理前の白金質量あたりのH2ガス吸着量をQ1、熱処理後の白金質量あたりのH2ガス吸着量をQ2とすると、次式(1)で表される。
 R=(Q1-Q2)/Q1×100      (1)
Regarding the catalysts for organic substance decomposition of Examples 1 to 8 and Comparative Examples 1 to 14 described above, the target loading amount of platinum, the adsorption amount of H 2 gas unit after heat treatment at 800 ° C., the adsorption amount of H 2 gas per platinum mass, and the heat treatment. H 2 gas adsorption amount per H 2 gas unit adsorption amount and the platinum mass before, and show a reduction rate of the H 2 gas adsorption amount per platinum mass by annealing 800 ° C. Table 9. The reduction rate R of the H 2 gas adsorption amount per platinum mass due to the heat treatment is as follows, assuming that the H 2 gas adsorption amount per platinum mass before the heat treatment is Q1 and the H 2 gas adsorption amount per platinum mass after the heat treatment is Q2. It is represented by the formula (1).
R = (Q1-Q2) / Q1 × 100 (1)
Figure JPOXMLDOC01-appb-T000009
Figure JPOXMLDOC01-appb-T000009
 表9に示すように、本発明の要件を満たしていない比較例1~14の有機物分解用触媒は、800℃の熱処理前後における白金質量あたりのH2ガス吸着量の低下率が94%以上と大きくなった。これに対して、本発明の要件を満たす実施例1~8の有機物分解用触媒は、800℃の熱処理前後における白金質量あたりのH2ガス吸着量の低下率が61%以上94%以下となった。すなわち、本発明の要件を満たす実施例1~8の有機物分解用触媒は、800℃のような高温環境下で使用された場合のH2ガス吸着量の低下を抑制して、触媒活性の低下を抑制することができる。 As shown in Table 9, the catalysts for organic matter decomposition of Comparative Examples 1 to 14 which do not satisfy the requirements of the present invention have a reduction rate of H 2 gas adsorption amount per platinum mass of 94% or more before and after the heat treatment at 800 ° C. I grew up. On the other hand, in the catalysts for organic matter decomposition of Examples 1 to 8 satisfying the requirements of the present invention, the reduction rate of the amount of H 2 gas adsorbed per platinum mass before and after the heat treatment at 800 ° C. is 61% or more and 94% or less. It was. That is, the catalysts for decomposing organic substances of Examples 1 to 8 satisfying the requirements of the present invention suppress the decrease in the amount of H 2 gas adsorbed when used in a high temperature environment such as 800 ° C., and decrease the catalytic activity. Can be suppressed.
 また、表9に示すように、実施例1~8の有機物分解用触媒は、800℃で熱処理した後における白金質量あたりのH2ガス吸着量が0.46cm3/g以上1.61cm3/g以下である。 Further, as shown in Table 9, Example 1 organic decomposition catalyst of 1-8, 800 H 2 gas adsorption amount per platinum mass in after heat treatment at ℃ is 0.46 cm 3 / g or more 1.61cm 3 / It is less than or equal to g.
 また、上述した実施例1~8および比較例1~14の有機物分解用触媒について、白金の目標担持量、800℃の熱処理後における白金の分散度、および、熱処理前における白金の分散度を表10に示す。 Further, for the catalysts for organic matter decomposition of Examples 1 to 8 and Comparative Examples 1 to 14 described above, the target carrying amount of platinum, the dispersity of platinum after the heat treatment at 800 ° C., and the dispersity of platinum before the heat treatment are shown. Shown in 10.
Figure JPOXMLDOC01-appb-T000010
Figure JPOXMLDOC01-appb-T000010
 また、実施例1~4、6、比較例1~5、7の有機物分解用触媒について、白金の目標担持量と、白金粒子の平均粒径を表11に示す。実施例1~4、6、および、比較例7の有機物分解用触媒については、白金粒子の粒径の標準偏差、最小値、および、最大値も示している。 Table 11 shows the target loading amount of platinum and the average particle size of platinum particles for the catalysts for organic matter decomposition in Examples 1 to 4, 6 and Comparative Examples 1 to 5, 7. For the catalysts for organic matter decomposition of Examples 1 to 4, 6 and Comparative Example 7, the standard deviation, the minimum value, and the maximum value of the particle size of the platinum particles are also shown.
Figure JPOXMLDOC01-appb-T000011
Figure JPOXMLDOC01-appb-T000011
 表11に示すように、実施例1~4および6の有機物分解用触媒の白金粒子の平均粒径は、28nm以上41nm以下である。なお、実施例5、7および8の有機物分解用触媒の白金粒子の平均粒径が28nm以上41nm以下であることも確認済みである。 As shown in Table 11, the average particle size of the platinum particles of the catalysts for organic matter decomposition in Examples 1 to 4 and 6 is 28 nm or more and 41 nm or less. It has also been confirmed that the average particle size of the platinum particles of the catalysts for decomposition of organic substances in Examples 5, 7 and 8 is 28 nm or more and 41 nm or less.
 図12は、実施例1~4と比較例1~5の有機物分解用触媒の白金粒子の平均粒径と、800℃の熱処理後における白金質量あたりのH2ガス吸着量との関係を示す図である。図12に示すように、本発明の要件を満たす実施例1~4の有機物分解用触媒は、本発明の要件を満たしていない比較例1~5の有機物分解用触媒と比べて、800℃の熱処理後における白金質量あたりのH2ガス吸着量が多いことが分かる。 FIG. 12 is a diagram showing the relationship between the average particle size of platinum particles of the catalysts for organic matter decomposition of Examples 1 to 4 and Comparative Examples 1 to 5 and the amount of H 2 gas adsorbed per platinum mass after heat treatment at 800 ° C. Is. As shown in FIG. 12, the organic matter decomposition catalysts of Examples 1 to 4 satisfying the requirements of the present invention have a temperature of 800 ° C. as compared with the organic matter decomposition catalysts of Comparative Examples 1 to 5 which do not satisfy the requirements of the present invention. It can be seen that the amount of H 2 gas adsorbed per platinum mass after the heat treatment is large.
 図13は、実施例1~8と比較例6~9の有機物分解用触媒について、800℃の熱処理後における白金質量あたりのH2ガス吸着量と、同等の白金担持量を有する比較例の有機物分解用触媒と比べたときの、800℃の熱処理後におけるH2ガス単位吸着量の比P1との関係を示す図である。上記H2ガス単位吸着量の比P1は、実施例1~8の有機物分解用触媒の800℃の熱処理後におけるH2ガス単位吸着量をK1、その有機物分解用触媒と同等の白金担持量を有する比較例(比較例6~9のいずれか)の有機物分解用触媒の800℃の熱処理後におけるH2ガス単位吸着量をK2としたときに、K1/K2で表される。比較例6~9の有機物分解用触媒についての上記H2ガス単位吸着量の比P1は、1である。 FIG. 13 shows the organic substances of Comparative Examples having the same amount of platinum supported as the amount of H 2 gas adsorbed per platinum mass after heat treatment at 800 ° C. for the catalysts for decomposition of organic substances of Examples 1 to 8 and Comparative Examples 6 to 9. when compared to cracking catalyst is a diagram showing the relationship between the ratio P1 of the H 2 gas unit amount of adsorption after heat treatment of 800 ° C.. The ratio P1 of the H 2 gas unit adsorption amount, the H 2 gas unit amount of adsorption after heat treatment 800 ° C. of the catalyst for decomposing organic substances of Examples 1 ~ 8 K1, the amount of platinum supported equivalent to their organic decomposition catalyst It is represented by K1 / K2 when the amount of H 2 gas unit adsorbed after the heat treatment of the organic substance decomposition catalyst of Comparative Example (any of Comparative Examples 6 to 9) at 800 ° C. is K2. The ratio P1 of the H 2 gas unit adsorption amount for the organic matter decomposition catalysts of Comparative Examples 6 to 9 is 1.
 図14は、実施例1~8と比較例11~14の有機物分解用触媒について、800℃の熱処理後における白金質量あたりのH2ガス吸着量と、同等の白金担持量を有する比較例の有機物分解用触媒と比べたときに、800℃の熱処理後におけるH2ガス単位吸着量の比P2との関係を示す図である。上記H2ガス単位吸着量の比P2は、実施例1~8の有機物分解用触媒の800℃の熱処理後におけるH2ガス単位吸着量をK1、その有機物分解用触媒と同等の白金担持量を有する比較例(比較例11~14のいずれか)の有機物分解用触媒の800℃の熱処理後におけるH2ガス単位吸着量をK3としたときに、K1/K3で表される。比較例11~14の有機物分解用触媒についての上記H2ガス単位吸着量の比P2は、1である。 FIG. 14 shows the organic substances of Comparative Examples of Examples 1 to 8 and Comparative Examples 11 to 14 having the same amount of H 2 gas adsorbed per platinum mass after heat treatment at 800 ° C. and the same amount of platinum supported. It is a figure which shows the relationship with the ratio P2 of the H 2 gas unit adsorption amount after the heat treatment at 800 degreeC when compared with the decomposition catalyst. The H 2 gas unit adsorption ratio P2 is H 2 gas unit amount of adsorption after heat treatment 800 ° C. of the catalyst for decomposing organic substances of Examples 1 ~ 8 K1, the amount of platinum supported equivalent to their organic decomposition catalyst It is represented by K1 / K3 when the amount of H 2 gas unit adsorbed after the heat treatment of the organic substance decomposition catalyst of Comparative Example (any of Comparative Examples 11 to 14) at 800 ° C. is K3. The ratio P2 of the H 2 gas unit adsorption amount for the organic matter decomposition catalysts of Comparative Examples 11 to 14 is 1.
 図14に示すように、本発明の要件を満たす実施例1~8の有機物分解用触媒は、比較例11~14の有機物分解用触媒と比べて、800℃の熱処理後におけるH2ガス単位吸着量が多い。 As shown in FIG. 14, the organic matter decomposition catalysts of Examples 1 to 8 satisfying the requirements of the present invention adsorb H 2 gas units after heat treatment at 800 ° C. as compared with the organic matter decomposition catalysts of Comparative Examples 11 to 14. The amount is large.
 本発明の要件を満たす有機物分解用触媒は、担体に含まれる窒化アルミニウムの表面は容易に酸化しない白金ナノ粒子が一面に高い分散度で担持されているため、800℃のような高温環境下で使用されても、窒化アルミニウムの酸化を抑制することができる。したがって、窒化アルミニウムの熱伝導率は維持されるので、高温環境下で使用された場合でも放熱が進み、担持されている白金の焼結を抑制することができる。これにより、白金の分散度の低下を抑制(シンタリングを抑制)することができ、触媒活性の低下を抑制することができる。 In the catalyst for organic substance decomposition that satisfies the requirements of the present invention, platinum nanoparticles that do not easily oxidize are supported on one surface of aluminum nitride contained in the carrier with a high degree of dispersion, so that the catalyst can be used in a high temperature environment such as 800 ° C. Even if it is used, it can suppress the oxidation of aluminum nitride. Therefore, since the thermal conductivity of aluminum nitride is maintained, heat dissipation proceeds even when the aluminum nitride is used in a high temperature environment, and the sintering of the supported platinum can be suppressed. Thereby, the decrease in the dispersity of platinum can be suppressed (sintering can be suppressed), and the decrease in the catalytic activity can be suppressed.
 上述したように、本発明の要件を満たす実施例1~8の有機物分解用触媒の白金粒子の平均粒径は、28nm以上41nm以下である。したがって、本発明の要件を満たす有機物分解用触媒は、白金粒子の平均粒径が28nm以上41nm以下であることが好ましい。 As described above, the average particle size of the platinum particles of the catalysts for organic matter decomposition of Examples 1 to 8 satisfying the requirements of the present invention is 28 nm or more and 41 nm or less. Therefore, in the catalyst for organic matter decomposition that satisfies the requirements of the present invention, it is preferable that the average particle size of platinum particles is 28 nm or more and 41 nm or less.
 本発明は、上記実施形態に限定されるものではなく、本発明の範囲内において、種々の応用、変形を加えることが可能である。 The present invention is not limited to the above embodiment, and various applications and modifications can be added within the scope of the present invention.
1  担体
2  白金
10 有機物分解用触媒
1 Carrier 2 Platinum 10 Catalyst for decomposition of organic matter

Claims (6)

  1.  有機物を分解するために用いられる有機物分解用触媒であって、
     担体と、
     前記担体に担持された白金と、
    を備え、
     前記担体は、その表面に存在するNとAlの原子%比N/Alが0.40以上0.50以下である窒化アルミニウムを含むことを特徴とする有機物分解用触媒。
    A catalyst for decomposing organic matter used to decompose organic matter.
    With the carrier
    Platinum supported on the carrier and
    With
    The carrier is a catalyst for decomposition of organic substances, which comprises aluminum nitride having an atomic% ratio N / Al of N and Al present on the surface thereof of 0.40 or more and 0.50 or less.
  2.  前記白金の平均粒径は、28nm以上41nm以下であることを特徴とする請求項1に記載の有機物分解用触媒。 The catalyst for organic matter decomposition according to claim 1, wherein the average particle size of the platinum is 28 nm or more and 41 nm or less.
  3.  H2ガスを導入して前記有機物分解用触媒に吸着されるH2ガスの吸着量を確認したときに、前記有機物分解用触媒を800℃で熱処理する前後において、前記有機物分解用触媒に吸着されるH2ガスの前記白金の質量あたりの吸着量の低下率は、61%以上94%以下であることを特徴とする請求項1または2に記載の有機物分解用触媒。 When the amount of H 2 gas adsorbed on the organic substance decomposition catalyst is confirmed by introducing H 2 gas, the organic substance decomposition catalyst is adsorbed on the organic substance decomposition catalyst before and after the heat treatment at 800 ° C. The catalyst for organic substance decomposition according to claim 1 or 2, wherein the rate of decrease in the adsorption amount of the H 2 gas per mass of the platinum is 61% or more and 94% or less.
  4.  H2ガスを導入して前記有機物分解用触媒に吸着されるH2ガスの吸着量を確認したときに、800℃で熱処理した後の前記有機物分解用触媒に吸着されるH2ガスの前記白金の質量あたりの吸着量は、0.46cm3/g以上1.61cm3/g以下であることを特徴とする請求項1~3のいずれかに記載の有機物分解用触媒。 When introducing the H 2 gas was confirmed adsorption amount of H 2 gas to be adsorbed to the organic material cracking catalyst, the platinum of the H 2 gas to be adsorbed to the organic material cracking catalyst after heat treatment at 800 ° C. adsorption amount per mass, 0.46 cm 3 / g or more 1.61cm 3 / g organic decomposition catalyst according to any one of claims 1 to 3, wherein the less.
  5.  塩素が含まれないことを特徴とする請求項1~4のいずれかに記載の有機物分解用触媒。 The catalyst for decomposing organic substances according to any one of claims 1 to 4, which is characterized by containing no chlorine.
  6.  請求項1~5のいずれかに記載の有機物分解用触媒を備えることを特徴とする有機物分解装置。 An organic matter decomposition apparatus comprising the catalyst for organic matter decomposition according to any one of claims 1 to 5.
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Citations (2)

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WO2002078840A1 (en) * 2001-03-29 2002-10-10 Idemitsu Kosan Co., Ltd. Catalyst for reforming hydrocarbon and method for preparation thereof, and process for reforming hydrocarbon using said catalyst
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WO2002078840A1 (en) * 2001-03-29 2002-10-10 Idemitsu Kosan Co., Ltd. Catalyst for reforming hydrocarbon and method for preparation thereof, and process for reforming hydrocarbon using said catalyst
CN101837304A (en) * 2010-04-29 2010-09-22 清华大学 Carrier for preparing syngas Ni-based catalyst through methane partial oxidation

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