JP2018202405A - Catalyst structure for volatile organic substance and method for producing the same and device for removing volatile organic substance - Google Patents

Catalyst structure for volatile organic substance and method for producing the same and device for removing volatile organic substance Download PDF

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JP2018202405A
JP2018202405A JP2018105688A JP2018105688A JP2018202405A JP 2018202405 A JP2018202405 A JP 2018202405A JP 2018105688 A JP2018105688 A JP 2018105688A JP 2018105688 A JP2018105688 A JP 2018105688A JP 2018202405 A JP2018202405 A JP 2018202405A
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volatile organic
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JP7295616B2 (en
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禎宏 加藤
Sadahiro Kato
禎宏 加藤
將行 福嶋
Masayuki Fukushima
將行 福嶋
尋子 高橋
Hiroko Takahashi
尋子 高橋
祐一郎 馬場
Yuichiro Baba
祐一郎 馬場
可織 関根
Kaori Sekine
可織 関根
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Furukawa Electric Co Ltd
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Abstract

To provide a catalyst structure for a volatile organic substance which can suppress the deterioration of catalytic activity, prevent the deactivation of catalytic functions by facilitating the removal of catalyst poison and prevent leakage of a catalyst from a catalyst structure and a method for producing the same and to provide a device for removing volatile organic substances.SOLUTION: There is provided a catalyst structure for a volatile organic substance which comprises a carrier with a porous structure composed of a zeolite-type compound and at least one catalyst for oxidation of volatile organic substances which is inherent in the carrier and composed of a metal, wherein the carrier has mutually communicating passages and the catalyst for oxidation of volatile organic substances is at least present in the passages of the carrier.SELECTED DRAWING: Figure 1

Description

本発明は、多孔質構造の担体と揮発性有機物質用触媒とを備える揮発性有機物質用触媒構造体及びその製造方法ならびに揮発性有機物質除去装置に関する。   The present invention relates to a catalyst structure for a volatile organic substance comprising a porous structure carrier and a catalyst for a volatile organic substance, a method for producing the same, and a volatile organic substance removing apparatus.

近年の環境意識の高まりに伴い、空気浄化の需要が高まっており、揮発性有機物質(以下、「VOC」ということがある。)の除去が要求されている。VOCとしては、例えば、トルエン、ベンゼン、フロン類、ジクロロメタン等が挙げられ、これらは、溶剤、燃料として重要な物質であることから、広汎に利用されている。しかし、VOCが環境中へ放出されると、公害などの健康被害を引き起こす。   With the recent increase in environmental awareness, the demand for air purification is increasing, and the removal of volatile organic substances (hereinafter sometimes referred to as “VOC”) is required. Examples of VOCs include toluene, benzene, chlorofluorocarbons, and dichloromethane. These are widely used because they are important substances as solvents and fuels. However, when VOC is released into the environment, it causes health damage such as pollution.

そこで、VOCの触媒による除去が検討されており、例えば、酸化反応によるVOCの除去が検討されている。上記触媒としては、高い触媒活性と安定性の観点からPt系触媒が使用されている。一方で、Pt系触媒は高価なので、Pt系触媒に代えて、非貴金属系触媒の使用も検討されている。しかし、非貴金属系触媒は、価格を低減できるが、反応温度がPt系触媒よりも高くなってしまう。   Therefore, removal of VOC by a catalyst has been studied. For example, removal of VOC by an oxidation reaction has been studied. As the catalyst, a Pt-based catalyst is used from the viewpoint of high catalytic activity and stability. On the other hand, since a Pt-based catalyst is expensive, use of a non-noble metal-based catalyst instead of a Pt-based catalyst has been studied. However, the cost of the non-noble metal-based catalyst can be reduced, but the reaction temperature becomes higher than that of the Pt-based catalyst.

非特許文献1では、Ptを担体に担持した触媒系であって優れた活性を示す触媒系が多く報告されている。   Non-Patent Document 1 reports many catalyst systems that support Pt on a carrier and exhibit excellent activity.

工業材料2017年1月号 Vol.65 No.1 p.71−74Industrial Materials January 2017 Vol. 65 No. 1 p. 71-74

しかしながら、上記のような従来の触媒構造体では、触媒粒子が担体の表面或いは表面近傍に担持されているため、VOC等を含む流体から受ける力や熱などの影響に因って触媒粒子が担体内で移動し、触媒粒子同士の凝集(シンタリング)が発生し易い。触媒粒子同士の凝集が生じると、触媒としての有効表面積が減少することで触媒活性が低下することから寿命が通常よりも短くなってしまう。さらに、触媒粒子同士の凝集により、VOC由来のNやS等を含む化合物である触媒毒を除去することが難しくなり、触媒機能が失活しやすい。   However, in the conventional catalyst structure as described above, since the catalyst particles are supported on or near the surface of the carrier, the catalyst particles are supported on the carrier due to the influence of the force and heat received from the fluid including VOC. The catalyst particles tend to agglomerate (sinter) between the catalyst particles. When aggregation of the catalyst particles occurs, the effective surface area as a catalyst decreases, and the catalyst activity decreases, so the life becomes shorter than usual. Furthermore, the aggregation of the catalyst particles makes it difficult to remove the catalyst poison, which is a compound containing N, S, and the like derived from VOC, and the catalyst function tends to be deactivated.

本発明の目的は、触媒活性の低下を抑制でき、触媒毒の除去を容易化することで触媒機能の失活を防止でき、触媒構造体から触媒が漏出することを防止できる揮発性有機物質用触媒構造体及びその製造方法ならびに揮発性有機物質除去装置を提供することにある。   It is an object of the present invention for a volatile organic substance that can suppress a decrease in catalyst activity, can prevent catalyst poisoning by facilitating removal of catalyst poisons, and can prevent the catalyst from leaking from the catalyst structure. It is an object of the present invention to provide a catalyst structure, a manufacturing method thereof, and a volatile organic substance removing device.

本発明者らは、上記目的を達成するために鋭意研究を重ねた結果、ゼオライト型化合物で構成される多孔質構造の担体と、前記担体に内在する少なくとも1つの金属からなる揮発性有機物質酸化触媒と、を備え、前記担体が、互いに連通する通路を有し、前記揮発性有機物質酸化触媒が、前記担体の少なくとも前記通路に存在していることによって、揮発性有機物質酸化触媒の触媒活性低下を抑制し、長寿命化を実現できる揮発性有機物質用触媒構造体が得られることを見出し、かかる知見に基づき本発明を完成させるに至った。   As a result of intensive studies to achieve the above object, the present inventors have obtained a porous structure carrier composed of a zeolite-type compound and oxidation of a volatile organic substance composed of at least one metal present in the carrier. A catalyst, and the carrier has a passage communicating with each other, and the volatile organic substance oxidation catalyst is present in at least the passage of the carrier. It has been found that a catalyst structure for a volatile organic substance capable of suppressing the decrease and realizing a long life can be obtained, and the present invention has been completed based on such knowledge.

すなわち、本発明の要旨構成は、以下のとおりである。
[1]ゼオライト型化合物で構成される多孔質構造の担体と、
前記担体に内在する少なくとも1つの、金属からなる揮発性有機物質酸化触媒と、
を備え、
前記担体が、互いに連通する通路を有し、
前記揮発性有機物質酸化触媒が、前記担体の少なくとも前記通路に存在していることを特徴とする揮発性有機物質用触媒構造体。
[2]前記通路は、前記ゼオライト型化合物の骨格構造によって画定される一次元孔、二次元孔及び三次元孔のうちのいずれかと、前記一次元孔、前記二次元孔及び前記三次元孔のうちのいずれとも異なる拡径部を有し、かつ
前記揮発性有機物質酸化触媒が、少なくとも前記拡径部に存在していることを特徴とする、上記[1]に記載の揮発性有機物質用触媒構造体。
[3]前記拡径部は、前記一次元孔、前記二次元孔及び前記三次元孔のうちのいずれかを構成する複数の孔同士を連通している、上記[2]に記載の揮発性有機物質用触媒構造体。
[4]前記揮発性有機物質酸化触媒が、金属微粒子であることを特徴とする、上記[2]又は[3]に記載の揮発性有機物質用触媒構造体。
[5]前記金属微粒子の平均粒径が、前記通路の平均内径よりも大きく、且つ前記拡径部の内径以下であることを特徴とする、上記[4]に記載の揮発性有機物質用触媒構造体。
[6]前記金属微粒子の金属元素(M)が、前記揮発性有機物質用触媒構造体に対して0.5〜2.5質量%で含有されていることを特徴とする、上記[5]に記載の揮発性有機物質用触媒構造体。
[7]前記金属微粒子の平均粒径が、0.08nm〜30nmであることを特徴とする、上記[4]〜[6]のいずれか1つに記載の揮発性有機物質用触媒構造体。
[8]前記金属微粒子の平均粒径が、0.4nm〜11.0nmであることを特徴とする、上記[7]に記載の揮発性有機物質用触媒構造体。
[9]前記通路の平均内径に対する前記金属微粒子の平均粒径の割合が、0.05 〜300であることを特徴とする、上記[4]〜[8]のいずれか1つに記載の揮発性有機物質用触媒構造体。
[10]前記通路の平均内径に対する前記金属微粒子の平均粒径の割合が、0.1 〜30であることを特徴とする、上記[9]に記載の揮発性有機物質用触媒構造体。
[11]前記通路の平均内径に対する前記金属微粒子の平均粒径の割合が、1.4〜3.6であることを特徴とする、上記[10]に記載の揮発性有機物質用触媒構造体。
[12]前記通路の平均内径は、0.1nm〜1.5nmであり、
前記拡径部の内径は、0.5nm〜50nmであることを特徴とする、上記[2]〜[11]のいずれか1つに記載の揮発性有機物質用触媒構造体。
[13]前記担体の外表面に保持された少なくとも1つの他の揮発性有機物質酸化触媒を更に備えることを特徴とする、上記[1]〜[12]のいずれか1つに記載の揮発性有機物質用触媒構造体。
[14]前記担体に内在する前記少なくとも1つの揮発性有機物質酸化触媒の含有量が、前記担体の外表面に保持された前記少なくとも1つの他の揮発性有機物質酸化触媒の含有量よりも多いことを特徴とする、上記[13]に記載の揮発性有機物質用触媒構造体。
[15]前記ゼオライト型化合物は、ケイ酸塩化合物であることを特徴とする、上記[1]〜[14]のいずれか1つに記載の揮発性有機物質用触媒構造体。
[16]上記[1]〜[15]のいずれか1つに記載の揮発性有機物質用触媒構造体を有する、揮発性有機物質除去装置。
[17]ゼオライト型化合物で構成される多孔質構造の担体を得るための前駆体材料(A)に金属含有溶液が含浸された前駆体材料(B)を焼成する焼成工程と、
前記前駆体材料(B)を焼成して得られた前駆体材料(C)を水熱処理する水熱処理工程と、
前記水熱処理された前駆体材料(C)に還元処理を行う工程と、
を有することを特徴とする揮発性有機物質用触媒構造体の製造方法。
[18]前記焼成工程の前に、非イオン性界面活性剤を、前記前駆体材料(A)に対して50〜500質量%添加することを特徴とする、上記[17]に記載の揮発性有機物質用触媒構造体の製造方法。
[19]前記焼成工程の前に、前記前駆体材料(A)に前記金属含有溶液を複数回に分けて添加することで、前記前駆体材料(A)に前記金属含有溶液を含浸させることを特徴とする、上記[17]又は[18]に記載の揮発性有機物質用触媒構造体の製造方法。
[20]前記焼成工程の前に前記前駆体材料(A)に前記金属含有溶液を含浸させる際に、前記前駆体材料(A)に添加する前記金属含有溶液の添加量を、前記前駆体材料(A)に添加する前記金属含有溶液中に含まれる金属元素(M)に対する、前記前駆体材料(A)を構成するケイ素(Si)の比(原子数比Si/M)に換算して、10〜1000となるように調整することを特徴とする、上記[17]〜[19]のいずれか1つに記載の揮発性有機物質用触媒構造体の製造方法。
[21]前記水熱処理工程において、前記前駆体材料(C)と構造規定剤とを混合することを特徴とする、上記[17]に記載の揮発性有機物質用触媒構造体の製造方法。
[22]前記水熱処理工程が塩基性雰囲気下で行われることを特徴とする、上記[17]に記載の揮発性有機物質用触媒構造体の製造方法。
That is, the gist configuration of the present invention is as follows.
[1] a porous support composed of a zeolite-type compound;
At least one volatile organic substance oxidation catalyst comprising a metal inherent in the carrier;
With
The carrier has passages communicating with each other;
A catalyst structure for a volatile organic substance, wherein the volatile organic substance oxidation catalyst is present in at least the passage of the carrier.
[2] The passage includes any one of a one-dimensional hole, a two-dimensional hole, and a three-dimensional hole defined by a skeleton structure of the zeolite-type compound, and the one-dimensional hole, the two-dimensional hole, and the three-dimensional hole. The volatile organic substance according to [1], wherein the volatile organic substance oxidation catalyst is present at least in the enlarged diameter part. Catalyst structure.
[3] The volatile property according to [2], wherein the enlarged diameter portion communicates a plurality of holes constituting any one of the one-dimensional hole, the two-dimensional hole, and the three-dimensional hole. Catalyst structure for organic substances.
[4] The catalyst structure for volatile organic substances according to [2] or [3] above, wherein the volatile organic substance oxidation catalyst is fine metal particles.
[5] The catalyst for volatile organic substances according to the above [4], wherein an average particle diameter of the metal fine particles is larger than an average inner diameter of the passage and not more than an inner diameter of the expanded portion. Structure.
[6] The metal element (M) of the metal fine particles is contained in an amount of 0.5 to 2.5% by mass with respect to the catalyst structure for volatile organic substances, [5] The catalyst structure for volatile organic substances described in 1.
[7] The catalyst structure for volatile organic substances according to any one of [4] to [6] above, wherein an average particle diameter of the metal fine particles is 0.08 nm to 30 nm.
[8] The catalyst structure for volatile organic substances according to [7] above, wherein an average particle diameter of the metal fine particles is 0.4 nm to 11.0 nm.
[9] The volatilization according to any one of [4] to [8] above, wherein a ratio of an average particle diameter of the metal fine particles to an average inner diameter of the passage is 0.05 to 300. Catalyst structure for organic substances.
[10] The catalyst structure for volatile organic substances according to [9] above, wherein a ratio of an average particle diameter of the metal fine particles to an average inner diameter of the passage is 0.1 to 30.
[11] The catalyst structure for volatile organic substances according to [10] above, wherein a ratio of an average particle diameter of the metal fine particles to an average inner diameter of the passage is 1.4 to 3.6. .
[12] The average inner diameter of the passage is 0.1 nm to 1.5 nm,
The catalyst structure for volatile organic substances according to any one of [2] to [11] above, wherein an inner diameter of the expanded portion is 0.5 nm to 50 nm.
[13] The volatile property as described in any one of [1] to [12] above, further comprising at least one other volatile organic substance oxidation catalyst held on the outer surface of the carrier. Catalyst structure for organic substances.
[14] The content of the at least one volatile organic substance oxidation catalyst inherent in the carrier is greater than the content of the at least one other volatile organic substance oxidation catalyst held on the outer surface of the carrier. The catalyst structure for volatile organic substances according to [13] above, wherein
[15] The catalyst structure for volatile organic substances according to any one of [1] to [14], wherein the zeolite-type compound is a silicate compound.
[16] A volatile organic substance removing device having the volatile organic substance catalyst structure according to any one of [1] to [15].
[17] A firing step of firing a precursor material (B) obtained by impregnating a precursor material (A) with a metal-containing solution into a porous structure carrier composed of a zeolite-type compound;
A hydrothermal treatment step of hydrothermally treating the precursor material (C) obtained by firing the precursor material (B);
Performing a reduction treatment on the hydrothermally treated precursor material (C);
A process for producing a catalyst structure for volatile organic substances, comprising:
[18] The volatile material as described in [17] above, wherein a nonionic surfactant is added in an amount of 50 to 500 mass% with respect to the precursor material (A) before the firing step. A method for producing a catalyst structure for organic substances.
[19] Before the firing step, the precursor material (A) is impregnated with the metal-containing solution by adding the metal-containing solution to the precursor material (A) in a plurality of times. The method for producing a catalyst structure for volatile organic substances according to [17] or [18] above,
[20] When the precursor material (A) is impregnated with the metal-containing solution before the firing step, the amount of the metal-containing solution added to the precursor material (A) is changed to the precursor material. In terms of the ratio of silicon (Si) constituting the precursor material (A) to the metal element (M) contained in the metal-containing solution added to (A) (atomic ratio Si / M), It adjusts so that it may become 10-1000, The manufacturing method of the catalyst structure for volatile organic substances as described in any one of said [17]-[19] characterized by the above-mentioned.
[21] The method for producing a catalyst structure for a volatile organic substance according to the above [17], wherein the precursor material (C) and a structure directing agent are mixed in the hydrothermal treatment step.
[22] The method for producing a catalyst structure for a volatile organic substance according to [17], wherein the hydrothermal treatment step is performed in a basic atmosphere.

本発明によれば、触媒活性の低下を抑制でき、触媒毒の除去を容易化することで触媒機能の失活を防止でき、触媒構造体から触媒が漏出することを防止できる揮発性有機物質用触媒構造体及びその製造方法ならびに揮発性有機物質除去装置を提供することができる。   According to the present invention, it is possible to suppress a decrease in catalyst activity, to prevent the catalyst function from being deactivated by facilitating the removal of the catalyst poison, and to prevent the catalyst from leaking from the catalyst structure. A catalyst structure, a manufacturing method thereof, and a volatile organic substance removing device can be provided.

図1は、本発明の実施形態に係る揮発性有機物質用触媒構造体の内部構造が分かるように概略的に示したものであって、図1(a)は斜視図(一部を横断面で示す。)、図1(b)は部分拡大断面図である。FIG. 1 schematically shows the internal structure of a catalyst structure for a volatile organic substance according to an embodiment of the present invention. FIG. 1 (a) is a perspective view (partially cross-sectional view). 1 (b) is a partially enlarged sectional view. 図2は、図1の揮発性有機物質用触媒構造体の機能の一例を説明するための部分拡大断面図であり、図2(a)は篩機能、図2(b)は触媒能を説明する図である。2 is a partially enlarged sectional view for explaining an example of the function of the catalyst structure for a volatile organic substance in FIG. 1, FIG. 2 (a) is a sieving function, and FIG. It is a figure to do. 図3は、図1の揮発性有機物質用触媒構造体の製造方法の一例を示すフローチャートである。FIG. 3 is a flowchart showing an example of a method for producing the volatile organic substance catalyst structure of FIG. 図4は、図1の揮発性有機物質用触媒構造体の変形例を示す模式図である。FIG. 4 is a schematic view showing a modification of the catalyst structure for volatile organic substances in FIG.

以下、本発明の実施形態を、図面を参照しながら詳細に説明する。   Hereinafter, embodiments of the present invention will be described in detail with reference to the drawings.

[揮発性有機物質用触媒構造体の構成]
図1は、本発明の実施形態に係る揮発性有機物質用触媒構造体の構成を概略的に示す図であり、(a)は斜視図(一部を横断面で示す。)、(b)は部分拡大断面図である。なお、図1における揮発性有機物質用触媒構造体は、その一例を示すものであり、本発明に係る各構成の形状、寸法等は、図1のものに限られないものとする。
[Configuration of catalyst structure for volatile organic substances]
FIG. 1 is a diagram schematically showing a configuration of a catalyst structure for a volatile organic substance according to an embodiment of the present invention, in which (a) is a perspective view (a part is shown in cross section), (b). FIG. Note that the volatile organic substance catalyst structure in FIG. 1 shows an example thereof, and the shape, size, and the like of each component according to the present invention are not limited to those in FIG.

図1(a)に示されるように、揮発性有機物質用触媒構造体1は、ゼオライト型化合物で構成される多孔質構造の担体10と、該担体10に内在する、少なくとも1つの、揮発性有機物質酸化触媒物質である金属微粒子20とを備える。揮発性有機物質酸化触媒物質は、揮発性有機物質を酸化することで揮発性有機物質除去触媒として機能する。   As shown in FIG. 1 (a), a catalyst structure 1 for a volatile organic substance has a porous structure carrier 10 composed of a zeolite-type compound, and at least one volatile component present in the carrier 10. And metal fine particles 20 that are organic material oxidation catalyst materials. The volatile organic substance oxidation catalyst substance functions as a volatile organic substance removal catalyst by oxidizing the volatile organic substance.

揮発性有機物質用触媒構造体1において、複数の金属微粒子20,20,・・・は、担体10の多孔質構造の内部に存在している。金属微粒子については、詳しくは後述する。   In the catalyst structure 1 for volatile organic substances, the plurality of metal fine particles 20, 20,... Exist inside the porous structure of the carrier 10. Details of the metal fine particles will be described later.

担体10は、多孔質構造であり、図1(b)に示すように、好適には複数の孔11a,11a,・・・が形成されることにより、互いに連通する通路11を有する。ここで金属微粒子20は、担体10の少なくとも通路11に存在しており、好ましくは担体10の少なくとも通路11に保持されている。   The carrier 10 has a porous structure and, as shown in FIG. 1 (b), preferably has a plurality of holes 11a, 11a,. Here, the metal fine particles 20 are present in at least the passage 11 of the carrier 10, and are preferably held in at least the passage 11 of the carrier 10.

このような構成により、担体10内での金属微粒子20の移動が規制され、金属微粒子20、20同士の凝集が有効に防止されている。その結果、揮発性有機物質酸化触媒物質である金属微粒子20としての有効表面積の減少を効果的に抑制することができ、金属微粒子20の触媒活性は長期にわたって持続する。すなわち、揮発性有機物質用触媒構造体1によれば、揮発性有機物質酸化触媒物質である金属微粒子20の凝集による触媒活性の低下を抑制でき、揮発性有機物質用触媒構造体1としての長寿命化を図ることができる。また、揮発性有機物質用触媒構造体1の長寿命化により、揮発性有機物質用触媒構造体1の交換頻度を低減でき、使用済みの揮発性有機物質用触媒構造体1の廃棄量を大幅に低減することができ、省資源化を図ることができる。   With such a configuration, the movement of the metal fine particles 20 in the carrier 10 is restricted, and aggregation of the metal fine particles 20 and 20 is effectively prevented. As a result, a reduction in the effective surface area of the metal fine particles 20 that are volatile organic substance oxidation catalyst substances can be effectively suppressed, and the catalytic activity of the metal fine particles 20 lasts for a long time. That is, according to the catalyst structure 1 for volatile organic substances, it is possible to suppress a decrease in catalytic activity due to aggregation of the metal fine particles 20 that are volatile organic substance oxidation catalyst substances. Life can be extended. In addition, by extending the life of the volatile organic substance catalyst structure 1, the replacement frequency of the volatile organic substance catalyst structure 1 can be reduced, and the amount of used volatile organic substance catalyst structure 1 is greatly reduced. Can be reduced to save resources.

通常、揮発性有機物質用触媒構造体1を、VOCを含む流体の中で用いる場合、流体から外力を受ける可能性がある。この場合、金属微粒子20が、担体10の外表面に付着状態で保持されているだけであると、流体からの外力の影響で担体10の外表面から離脱しやすいという問題がある。これに対し、揮発性有機物質用触媒構造体1では、金属微粒子20は担体10の少なくとも通路11に存在しているため、流体による外力の影響を受けたとしても、担体10から金属微粒子20が離脱しにくい。すなわち、揮発性有機物質用触媒構造体1が流体内にある場合、流体は担体10の孔11aから、通路11内に流入するため、通路11内を流れる流体の速さは、流路抵抗(摩擦力)により、担体10の外表面を流れる流体の速さに比べて、遅くなると考えられる。このような流路抵抗の影響により、通路11内に存在する金属微粒子20が流体から受ける圧力は、担体10の外部において金属微粒子20が流体から受ける圧力に比べて低くなる。そのため、担体11に内在する金属微粒子20が離脱することを効果的に抑制でき、金属微粒子20の触媒活性を長期的に安定して維持することが可能となる。なお、上記のような流路抵抗は、担体10の通路11が、曲がりや分岐を複数有し、担体10の内部がより複雑で三次元的な立体構造となっているほど、大きくなると考えられる。   Usually, when the catalyst structure 1 for volatile organic substances is used in a fluid containing VOC, there is a possibility of receiving an external force from the fluid. In this case, if the metal fine particles 20 are only held in the attached state on the outer surface of the carrier 10, there is a problem that the metal fine particles 20 are easily detached from the outer surface of the carrier 10 due to the influence of the external force from the fluid. On the other hand, in the catalyst structure 1 for volatile organic substances, the metal fine particles 20 are present in at least the passage 11 of the carrier 10, so that even if the metal fine particles 20 are affected by an external force due to fluid, Difficult to leave. That is, when the volatile organic substance catalyst structure 1 is in the fluid, the fluid flows into the passage 11 from the hole 11a of the carrier 10, so that the speed of the fluid flowing in the passage 11 depends on the flow resistance ( The frictional force) is considered to be slower than the speed of the fluid flowing on the outer surface of the carrier 10. Due to the influence of the flow path resistance, the pressure that the metal fine particles 20 existing in the passage 11 receive from the fluid is lower than the pressure that the metal fine particles 20 receive from the fluid outside the carrier 10. Therefore, it is possible to effectively suppress the separation of the metal fine particles 20 existing in the carrier 11, and it is possible to stably maintain the catalytic activity of the metal fine particles 20 for a long period of time. The flow path resistance as described above is considered to increase as the passage 11 of the carrier 10 has a plurality of bends and branches and the inside of the carrier 10 has a more complicated and three-dimensional structure. .

また、通路11は、ゼオライト型化合物の骨格構造によって画定される一次元孔、二次元孔及び三次元孔のうちのいずれかと、上記一次元孔、上記二次元孔及び上記三次元孔のうちのいずれとも異なる拡径部12とを有していることが好ましく、このとき、金属微粒子20は、少なくとも拡径部12に存在していることが好ましく、少なくとも拡径部12に包接されていることがより好ましい。ここでいう一次元孔とは、一次元チャンネルを形成しているトンネル型またはケージ型の孔、もしくは複数の一次元チャンネルを形成しているトンネル型またはケージ型の複数の孔(複数の一次元チャンネル)を指す。また、二次元孔とは、複数の一次元チャンネルが二次元的に連結された二次元チャンネルを指し、三次元孔とは、複数の一次元チャンネルが三次元的に連結された三次元チャンネルを指す。これにより、金属微粒子20の担体10内での移動がさらに規制され、金属微粒子20の離脱や、金属微粒子20、20同士の凝集をさらに有効に防止することができる。包接とは、金属微粒子20が担体10に内包されている状態を指す。このとき金属微粒子20と担体10とは、必ずしも直接的に互いが接触している必要はなく、金属微粒子20と担体10との間に他の物質(例えば、界面活性剤等)が介在した状態で、金属微粒子20が担体10に間接的に存在していてもよい。   Further, the passage 11 includes any one of a one-dimensional hole, a two-dimensional hole, and a three-dimensional hole defined by a skeleton structure of the zeolite type compound, and the one-dimensional hole, the two-dimensional hole, and the three-dimensional hole. Preferably, the metal fine particles 20 are present at least in the diameter-expanded portion 12, and are at least included in the diameter-expanded portion 12. It is more preferable. As used herein, a one-dimensional hole means a tunnel-type or cage-type hole forming a one-dimensional channel, or a plurality of tunnel-type or cage-type holes forming a plurality of one-dimensional channels (a plurality of one-dimensional holes). Channel). A two-dimensional hole refers to a two-dimensional channel in which a plurality of one-dimensional channels are two-dimensionally connected. A three-dimensional hole refers to a three-dimensional channel in which a plurality of one-dimensional channels are three-dimensionally connected. Point to. Thereby, the movement of the metal fine particles 20 in the carrier 10 is further restricted, and the separation of the metal fine particles 20 and the aggregation of the metal fine particles 20, 20 can be more effectively prevented. Inclusion refers to a state in which the metal fine particles 20 are encapsulated in the carrier 10. At this time, the metal fine particles 20 and the carrier 10 are not necessarily in direct contact with each other, and another substance (for example, a surfactant or the like) is interposed between the metal fine particles 20 and the carrier 10. Thus, the metal fine particles 20 may be present indirectly on the carrier 10.

図1(b)では金属微粒子20が拡径部12に存在している場合を示しているが、この構成だけには限定されず、金属微粒子20は、その一部が拡径部12の外側にはみ出した状態で通路11に存在していてもよい。また、金属微粒子20は、拡径部12以外の通路11の部分(例えば通路11の内壁部分)に部分的に埋設され、または固着等によって存在していてもよい。
また、拡径部12は、上記一次元孔、上記二次元孔及び上記三次元孔のうちのいずれかを構成する複数の孔11a,11a同士を連通しているのが好ましい。これにより、担体10の内部に、一次元孔、二次元孔又は三次元孔とは異なる別途の通路が設けられるので、金属微粒子20の機能をより発揮させることができる。
Although FIG. 1B shows a case where the metal fine particles 20 are present in the enlarged diameter portion 12, the present invention is not limited to this configuration, and a part of the metal fine particles 20 is outside the enlarged diameter portion 12. You may exist in the channel | path 11 in the state which protruded. Further, the metal fine particles 20 may be partially embedded in a portion of the passage 11 other than the enlarged diameter portion 12 (for example, an inner wall portion of the passage 11), or may be present by fixing or the like.
Moreover, it is preferable that the enlarged diameter part 12 is connecting the some hole 11a and 11a which comprise either of the said one-dimensional hole, the said two-dimensional hole, and the said three-dimensional hole. Thereby, since the separate channel | path different from a one-dimensional hole, a two-dimensional hole, or a three-dimensional hole is provided in the inside of the support | carrier 10, the function of the metal microparticle 20 can be exhibited more.

また、通路11は、担体10の内部に、分岐部または合流部を含んで三次元的に形成されており、拡径部12は、通路11の上記分岐部または合流部に設けられるのが好ましい。   The passage 11 is formed in a three-dimensional manner inside the carrier 10 including a branch portion or a merge portion, and the enlarged diameter portion 12 is preferably provided in the branch portion or the merge portion of the passage 11. .

担体10に形成された通路11の平均内径Dは、上記一次元孔、二次元孔及び三次元孔のうちのいずれかを構成する孔11aの短径及び長径の平均値から算出され、例えば0.1nm〜1.5nmであり、好ましくは0.5nm〜0.8nmである。また、拡径部12の内径Dは、例えば0.5nm〜50nmであり、好ましくは1.1nm〜40nm、より好ましくは1.1nm〜3.3nmである。拡径部12の内径Dは、例えば後述する前駆体材料(A)の細孔径、及び存在する金属微粒子20の平均粒径Dに依存する。拡径部12の内径Dは、金属微粒子20が存在し得る大きさである。 The average inner diameter DF of the passage 11 formed in the carrier 10 is calculated from the average value of the short diameter and the long diameter of the hole 11a constituting any one of the one-dimensional hole, the two-dimensional hole, and the three-dimensional hole. The thickness is 0.1 nm to 1.5 nm, preferably 0.5 nm to 0.8 nm. Further, the inner diameter DE of the enlarged diameter portion 12 is, for example, 0.5 nm to 50 nm, preferably 1.1 nm to 40 nm, and more preferably 1.1 nm to 3.3 nm. The inner diameter D E of the enlarged diameter portion 12 is, for example pore size of which will be described later precursor material (A), and on the average particle diameter D C of the fine metal particles 20 present. The inner diameter DE of the enlarged diameter portion 12 is a size that allows the metal fine particles 20 to exist.

担体10は、ゼオライト型化合物で構成される。ゼオライト型化合物としては、例えば、ゼオライト(アルミノケイ酸塩)、陽イオン交換ゼオライト、シリカライト等のケイ酸塩化合物、アルミノホウ酸塩、アルミノヒ酸塩、ゲルマニウム酸塩等のゼオライト類縁化合物、リン酸モリブデン等のリン酸塩系ゼオライト類似物質などが挙げられる。中でも、ゼオライト型化合物はケイ酸塩化合物であることが好ましい。   The carrier 10 is composed of a zeolite type compound. Zeolite type compounds include, for example, zeolites (aluminosilicates), cation exchange zeolites, silicate compounds such as silicalite, zeolite related compounds such as aluminoborate, aluminoarsenate, germanate, molybdenum phosphate, etc. And phosphate-based zeolite-like substances. Among these, the zeolite type compound is preferably a silicate compound.

ゼオライト型化合物の骨格構造は、FAU型(Y型またはX型)、MTW型、MFI型(ZSM−5)、FER型(フェリエライト)、LTA型(A型)、MWW型(MCM−22)、MOR型(モルデナイト)、LTL型(L型)、BEA型(ベータ型)などの中から選択され、好ましくはMFI型であり、より好ましくはZSM−5である。ゼオライト型化合物には、各骨格構造に応じた孔径を有する孔が複数形成されており、例えばMFI型の最大孔径は0.636nm(6.36Å)、平均孔径0.560nm(5.60Å)である。   The framework structure of zeolite type compounds is FAU type (Y type or X type), MTW type, MFI type (ZSM-5), FER type (ferrierite), LTA type (A type), MWW type (MCM-22) , MOR type (mordenite), LTL type (L type), BEA type (beta type), etc., preferably MFI type, more preferably ZSM-5. In the zeolite type compound, a plurality of pores having a pore size corresponding to each skeleton structure are formed. For example, the maximum pore size of the MFI type is 0.636 nm (6.36 mm), and the average pore size is 0.560 nm (5.60 mm). is there.

以下、揮発性有機物質酸化触媒物質である金属微粒子20について詳しく説明する。   Hereinafter, the metal fine particles 20 which are volatile organic substance oxidation catalyst substances will be described in detail.

金属微粒子20は一次粒子である場合と、一次粒子が凝集して形成した二次粒子である場合とがあるが、金属微粒子20の平均粒径Dは、好ましくは通路11の平均内径Dよりも大きく、且つ拡径部12の内径D以下である(D<D≦D)。このような金属微粒子20は、通路11内では、拡径部12に存在し、好適には包接されており、担体10内での金属微粒子20の移動が規制される。よって、金属微粒子20が流体から外力を受けた場合であっても、担体10内での金属微粒子20の移動が抑制され、担体10の通路11に分散配置された拡径部12、12、・・のそれぞれに存在する金属微粒子20、20、・・同士が接触するのを有効に防止することができる。 And when the fine metal particles 20 are primary particles, but there is the case the primary particle is a secondary particle formed by aggregation, the average particle diameter D C of the fine metal particles 20 have an average internal diameter D F of the preferred path 11 Larger than the inner diameter D E of the enlarged diameter portion 12 (D F <D C ≦ D E ). Such metal fine particles 20 are present in the diameter-expanded portion 12 in the passage 11 and are preferably enclosed, and the movement of the metal fine particles 20 in the carrier 10 is restricted. Therefore, even when the metal fine particle 20 receives an external force from the fluid, the movement of the metal fine particle 20 in the carrier 10 is suppressed, and the diameter-enlarged portions 12, 12,. It is possible to effectively prevent the metal fine particles 20, 20,.

また、金属微粒子20の平均粒径Dは、一次粒子および二次粒子のいずれの場合も、好ましくは0.08nm〜30nmであり、より好ましくは0.08nm以上25nm未満であり、さらに好ましくは0.4nm〜11.0nmであり、特に好ましくは0.8nm〜2.7nmである。また、通路11の平均内径Dに対する金属微粒子20の平均粒径Dの割合(D/D)は、好ましくは0.05〜300であり、より好ましくは0.1〜30であり、更に好ましくは1.1〜30であり、特に好ましくは1.4〜3.6である。
また、揮発性有機物質酸化触媒物質20が金属微粒子である場合、金属微粒子の金属元素(M)は、揮発性有機物質用触媒構造体1に対して0.5〜2.5質量%で含有されているのが好ましく、揮発性有機物質用触媒構造体1に対して0.5〜1.5質量%で含有されているのがより好ましい。例えば、金属元素(M)がCoである場合、Co元素の含有量(質量%)は、[(Co元素の質量)/(揮発性有機物質用触媒構造体1の全元素の質量)]×100で表される。
The average particle diameter D C of the fine metal particles 20, in either case of the primary particles and secondary particles, preferably 0.08Nm~30nm, more preferably less than than 0.08 nm 25 nm, more preferably It is 0.4 nm-11.0 nm, Most preferably, it is 0.8 nm-2.7 nm. The ratio of the average particle diameter D C of the fine metal particles 20 to the average inner diameter D F of the passage 11 (D C / D F) is preferably from 0.05 to 300, more preferably 0.1 to 30 More preferably, it is 1.1-30, Most preferably, it is 1.4-3.6.
Moreover, when the volatile organic substance oxidation catalyst substance 20 is a metal fine particle, the metal element (M) of the metal fine particle is contained at 0.5 to 2.5 mass% with respect to the catalyst structure 1 for a volatile organic substance. It is preferable that it is contained in an amount of 0.5 to 1.5% by mass with respect to the catalyst structure 1 for volatile organic substances. For example, when the metal element (M) is Co, the content (mass%) of the Co element is [(mass of Co element) / (mass of all elements of the volatile organic substance catalyst structure 1)] × 100.

上記金属微粒子20は、酸化されていない金属で構成されていればよく、例えば、単一の金属で構成されていてもよく、あるいは2種以上の金属の混合物で構成されていてもよい。なお、本明細書において、金属微粒子を構成する(材質としての)「金属」は、1種の金属元素(M)を含む単体金属と、2種以上の金属元素(M)を含む金属合金とを含む意味であり、1種以上の金属元素を含む金属の総称である。   The metal fine particles 20 may be composed of a metal that is not oxidized, and may be composed of, for example, a single metal or a mixture of two or more metals. In this specification, “metal” (as a material) constituting the metal fine particles includes a single metal containing one kind of metal element (M), a metal alloy containing two or more kinds of metal elements (M), and Is a generic term for metals containing one or more metal elements.

このような金属としては、例えば白金(Pt)、パラジウム(Pd)、ルテニウム(Ru)、ロジウム(Rh)、銀(Ag)等が挙げられ、上記のいずれか1種以上を主成分とすることが好ましい。   Examples of such a metal include platinum (Pt), palladium (Pd), ruthenium (Ru), rhodium (Rh), silver (Ag), and the like, and any one or more of the above as a main component. Is preferred.

また、金属微粒子20を構成する金属元素(M)に対する、担体10を構成するケイ素(Si)の割合(原子数比Si/M)は、10〜1000であるのが好ましく、50〜200であるのがより好ましい。上記割合が1000より大きいと、活性が低く、揮発性有機物質酸化触媒物質としての作用が十分に得られない可能性がある。一方、上記割合が10よりも小さいと、金属微粒子20の割合が大きくなりすぎて、担体10の強度が低下する傾向がある。なお、ここでいう金属微粒子20は、担体10の内部に存在し、好適には保持され、または担持された微粒子をいい、担体10の外表面に付着した金属微粒子を含まない。   Further, the ratio of the silicon (Si) constituting the carrier 10 to the metal element (M) constituting the metal fine particle 20 (atomic number ratio Si / M) is preferably 10 to 1000, and preferably 50 to 200. Is more preferable. If the ratio is greater than 1000, the activity is low, and there is a possibility that the action as a volatile organic substance oxidation catalyst substance cannot be sufficiently obtained. On the other hand, if the ratio is less than 10, the ratio of the metal fine particles 20 becomes too large, and the strength of the carrier 10 tends to decrease. The metal fine particles 20 referred to here are fine particles that exist inside the carrier 10 and are preferably held or supported, and do not include the metal fine particles attached to the outer surface of the carrier 10.

[揮発性有機物質用触媒構造体の機能]
揮発性有機物質用触媒構造体1は、上記のとおり、多孔質構造の担体10と、担体に内在する少なくとも1つの金属微粒子20とを備える。揮発性有機物質用触媒構造体1は、担体に内在する金属微粒子20が流体と接触することにより、金属微粒子20の触媒活性に応じた触媒能を発揮する。具体的に、揮発性有機物質用触媒構造体1の外表面10aに接触した流体は、外表面10aに形成された孔11aから担体10内部に流入して通路11内に誘導され、通路11内を通って移動し、他の孔11aを通じて揮発性有機物質用触媒構造体1の外部へ出る。流体が通路11内を通って移動する経路において、通路11に存在する金属微粒子20と接触することによって、金属微粒子20の触媒能に応じた触媒反応が生じる。また、揮発性有機物質用触媒構造体1は、担体が多孔質構造であることにより、分子篩能を有する。
[Function of catalyst structure for volatile organic substances]
As described above, the volatile organic substance catalyst structure 1 includes a porous support 10 and at least one metal fine particle 20 present in the support. The catalyst structure 1 for a volatile organic substance exhibits catalytic ability corresponding to the catalytic activity of the metal fine particles 20 when the metal fine particles 20 existing in the carrier come into contact with the fluid. Specifically, the fluid that has contacted the outer surface 10a of the volatile organic substance catalyst structure 1 flows into the inside of the carrier 10 from the holes 11a formed in the outer surface 10a, and is guided into the passage 11 so that the inside of the passage 11 It moves through and goes out of the catalyst structure 1 for volatile organic substances through the other hole 11a. In the path in which the fluid moves through the passage 11, a catalytic reaction corresponding to the catalytic ability of the metal fine particles 20 occurs by contacting the metal fine particles 20 existing in the passage 11. Moreover, the catalyst structure 1 for volatile organic substances has molecular sieving ability because the carrier has a porous structure.

まず、揮発性有機物質用触媒構造体1の分子篩能について、図2(a)を用いて、流体がベンゼン、トルエン等の揮発性有機物質(VOC)を含む気体である場合を例として説明する。図2(a)に示すように、孔11aの孔径以下、言い換えれば、通路11の内径以下の大きさを有する分子で構成されるVOC(例えば、ベンゼン、トルエン等)は、担体10内に流入することができる。一方、孔11aの孔径を超える大きさを有する非VOC成分15は、担体10内へ流入することができない。このように、流体が複数種類の化合物を含んでいる場合に、担体10内に流入することができない化合物の反応は規制され、担体10内に流入することができる化合物を反応させることができる。   First, the molecular sieving ability of the catalyst structure 1 for a volatile organic substance will be described with reference to FIG. 2A, taking as an example the case where the fluid is a gas containing a volatile organic substance (VOC) such as benzene or toluene. . As shown in FIG. 2A, VOC (for example, benzene, toluene, etc.) composed of molecules having a size smaller than the diameter of the hole 11a, in other words, smaller than the inner diameter of the passage 11, flows into the carrier 10. can do. On the other hand, the non-VOC component 15 having a size exceeding the hole diameter of the hole 11 a cannot flow into the carrier 10. Thus, when the fluid contains a plurality of types of compounds, the reaction of the compound that cannot flow into the carrier 10 is restricted, and the compound that can flow into the carrier 10 can be reacted.

反応によって担体10内で生成した化合物のうち、孔11aの孔径以下の大きさを有する分子で構成される化合物のみが孔11aを通じて担体10の外部へ出ることができ、反応生成物として得られる。一方、孔11aから担体10の外部へ出ることができない化合物は、担体10の外部へ出ることができる大きさの分子で構成される化合物に変換させれば、担体10の外部へ出すことができる。このように、揮発性有機物質用触媒構造体1を用いることにより、特定の反応生成物を選択的に得ることができる。   Of the compounds produced in the carrier 10 by the reaction, only compounds composed of molecules having a size equal to or smaller than the pore diameter of the pores 11a can go out of the carrier 10 through the pores 11a and are obtained as reaction products. On the other hand, a compound that cannot go out of the carrier 10 through the holes 11a can be put out of the carrier 10 if converted into a compound composed of molecules of a size that can go out of the carrier 10. . Thus, a specific reaction product can be selectively obtained by using the catalyst structure 1 for volatile organic substances.

揮発性有機物質用触媒構造体1では、図2(b)に示すように、通路11の拡径部12に金属微粒子20が存在している。金属微粒子20の平均粒径Dが、通路11の平均内径Dよりも大きく、拡径部12の内径Dよりも小さい場合には(D<D<D)、金属微粒子20と拡径部12との間に小通路13が形成される。そこで、図2(b)中の矢印に示すように、小通路13に流入したVOCを含む流体が金属微粒子20と接触する。各金属微粒子20は、拡径部12に存在しているため、担体10内での移動が制限されている。これにより、担体10内における金属微粒子20、20同士の凝集が防止される。その結果、金属微粒子20と流体との大きな接触面積を安定して維持することができる。 In the catalyst structure 1 for volatile organic substances, the metal fine particles 20 are present in the enlarged diameter portion 12 of the passage 11 as shown in FIG. When the average particle diameter D C of the metal fine particles 20 is larger than the average inner diameter D F of the passage 11 and smaller than the inner diameter D E of the enlarged diameter portion 12 (D F <D C <D E ), the metal fine particles 20 A small passage 13 is formed between the small diameter portion 12 and the enlarged diameter portion 12. Therefore, as shown by the arrow in FIG. 2B, the fluid containing VOC flowing into the small passage 13 comes into contact with the metal fine particles 20. Since each metal fine particle 20 exists in the enlarged diameter part 12, the movement in the support | carrier 10 is restrict | limited. Thereby, aggregation of the metal fine particles 20 and 20 in the carrier 10 is prevented. As a result, a large contact area between the metal fine particles 20 and the fluid can be stably maintained.

そして、通路11に流入したVOCが金属微粒子20に接触すると、金属微粒子20による酸化分解反応によってVOCが酸化される。例えば、金属微粒子20に含まれるルテニウムを触媒とする場合、VOCを、二酸化炭素及び水等に分解して無害化する。このように金属微粒子20による酸化分解処理を行うことにより、VOCを無害化することができる。また、揮発性有機物質用触媒構造体1を用いて、揮発性有機物質除去装置が形成されてもよい。上記実施形態例に係る揮発性有機物質用触媒構造体1を用いることで、上記と同様の効果を奏する揮発性有機物質除去装置を得ることができる。   When the VOC flowing into the passage 11 comes into contact with the metal fine particles 20, the VOC is oxidized by an oxidative decomposition reaction by the metal fine particles 20. For example, when ruthenium contained in the metal fine particles 20 is used as a catalyst, VOC is decomposed into carbon dioxide and water to make them harmless. By performing the oxidative decomposition treatment with the metal fine particles 20 in this way, VOC can be rendered harmless. Moreover, the volatile organic substance removal apparatus may be formed using the catalyst structure 1 for volatile organic substances. By using the volatile organic substance catalyst structure 1 according to the above embodiment, a volatile organic substance removing apparatus that exhibits the same effect as described above can be obtained.

[揮発性有機物質用触媒構造体の製造方法]
図3は、図1の揮発性有機物質用触媒構造体1の製造方法を示すフローチャートである。以下、担体に内在する揮発性有機物質酸化触媒物質が金属微粒子である、揮発性有機物質用触媒構造体の製造方法の一例を説明する。
[Method for producing catalyst structure for volatile organic substances]
FIG. 3 is a flowchart showing a method of manufacturing the volatile organic substance catalyst structure 1 of FIG. Hereinafter, an example of a method for producing a catalyst structure for a volatile organic substance in which the volatile organic substance oxidation catalyst substance present in the carrier is metal fine particles will be described.

(ステップS1:準備工程)
図3に示すように、先ず、ゼオライト型化合物で構成される多孔質構造の担体を得るための前駆体材料(A)を準備する。前駆体材料(A)は、好ましくは規則性メソ細孔物質であり、揮発性有機物質用触媒構造体の担体を構成するゼオライト型化合物の種類(組成)に応じて適宜選択できる。
(Step S1: Preparation process)
As shown in FIG. 3, first, a precursor material (A) for obtaining a porous support composed of a zeolite-type compound is prepared. The precursor material (A) is preferably a regular mesoporous material, and can be appropriately selected according to the type (composition) of the zeolite-type compound constituting the carrier of the catalyst structure for volatile organic substances.

ここで、揮発性有機物質用触媒構造体の担体を構成するゼオライト型化合物がケイ酸塩化合物である場合には、規則性メソ細孔物質は、細孔径1〜50nmの細孔が1次元、2次元または3次元に均一な大きさかつ規則的に発達したSi−O骨格からなる化合物であることが好ましい。このような規則性メソ細孔物質は、合成条件によって様々な合成物として得られるが、合成物の具体例としては、例えばSBA−1、SBA−15、SBA−16、KIT−6、FSM−16、MCM−41等が挙げられ、中でもMCM−41が好ましい。なお、SBA−1の細孔径は10〜30nm、SBA−15の細孔径は6〜10nm、SBA−16の細孔径は6nm、KIT−6の細孔径は9nm、FSM−16の細孔径は3〜5nm、MCM−41の細孔径は1〜10nmである。また、このような規則性メソ細孔物質としては、例えばメソポーラスシリカ、メソポーラスアルミノシリケート、メソポーラスメタロシリケート等が挙げられる。   Here, when the zeolite-type compound constituting the carrier of the catalyst structure for volatile organic substances is a silicate compound, the regular mesoporous material has a one-dimensional pore having a pore diameter of 1 to 50 nm, A compound composed of a Si—O skeleton that is uniform in size in two or three dimensions and regularly developed is preferable. Such regular mesoporous materials can be obtained as various composites depending on the synthesis conditions. Specific examples of the composites include, for example, SBA-1, SBA-15, SBA-16, KIT-6, FSM- 16, MCM-41, etc., among which MCM-41 is preferable. The pore diameter of SBA-1 is 10 to 30 nm, the pore diameter of SBA-15 is 6 to 10 nm, the pore diameter of SBA-16 is 6 nm, the pore diameter of KIT-6 is 9 nm, and the pore diameter of FSM-16 is 3 -5 nm, MCM-41 has a pore diameter of 1-10 nm. Examples of such regular mesoporous materials include mesoporous silica, mesoporous aluminosilicate, and mesoporous metallosilicate.

前駆体材料(A)は、市販品および合成品のいずれであってもよい。前駆体材料(A)を合成する場合には、公知の規則性メソ細孔物質の合成方法により行うことができる。例えば、前駆体材料(A)の構成元素を含有する原料と、前駆体材料(A)の構造を規定するための鋳型剤とを含む混合溶液を調製し、必要に応じてpHを調整して、水熱処理(水熱合成)を行う。その後、水熱処理により得られた沈殿物(生成物)を回収(例えば、ろ別)し、必要に応じて洗浄および乾燥し、さらに焼成することで、粉末状の規則性メソ細孔物質である前駆体材料(A)が得られる。ここで、混合溶液の溶媒としては、例えば水、またはアルコール等の有機溶媒、若しくはこれらの混合溶媒等を用いることができる。また、原料は、担体の種類に応じて選択されるが、例えばテトラエトキシシラン(TEOS)等のシリカ剤、フュームドシリカ、石英砂等が挙げられる。また、鋳型剤としては、各種界面活性剤、ブロックコポリマー等を用いることができ、規則性メソ細孔物質の合成物の種類に応じて選択することが好ましく、例えばMCM−41を作製する場合にはヘキサデシルトリメチルアンモニウムブロミド等の界面活性剤が好適である。水熱処理は、例えば、密閉容器内で、80〜800℃、5時間〜240時間、0〜2000kPaの処理条件で行うことができる。焼成処理は、例えば、空気中で、350〜850℃、2〜30時間の処理条件で行うことができる。   The precursor material (A) may be a commercially available product or a synthetic product. When the precursor material (A) is synthesized, it can be performed by a known method for synthesizing regular mesoporous materials. For example, a mixed solution containing a raw material containing the constituent elements of the precursor material (A) and a templating agent for defining the structure of the precursor material (A) is prepared, and the pH is adjusted as necessary. Hydrothermal treatment (hydrothermal synthesis) is performed. Thereafter, the precipitate (product) obtained by hydrothermal treatment is recovered (for example, filtered), washed and dried as necessary, and further calcined to form a regular mesoporous material in powder form. A precursor material (A) is obtained. Here, as a solvent of the mixed solution, for example, water, an organic solvent such as alcohol, or a mixed solvent thereof can be used. Moreover, although a raw material is selected according to the kind of support | carrier, for example, silica agents, such as tetraethoxysilane (TEOS), fumed silica, quartz sand, etc. are mentioned. Further, as the templating agent, various surfactants, block copolymers and the like can be used, and it is preferable to select according to the type of the synthesized compound of regular mesoporous materials. For example, when preparing MCM-41 A surfactant such as hexadecyltrimethylammonium bromide is preferred. The hydrothermal treatment can be performed, for example, in a sealed container at 80 to 800 ° C., 5 hours to 240 hours, and treatment conditions of 0 to 2000 kPa. The baking treatment can be performed, for example, in air at 350 to 850 ° C. for 2 to 30 hours.

(ステップS2:含浸工程)
次に、準備した前駆体材料(A)に、金属含有溶液を含浸させ、前駆体材料(B)を得る。
(Step S2: impregnation step)
Next, the prepared precursor material (A) is impregnated with the metal-containing solution to obtain the precursor material (B).

金属含有溶液は、揮発性有機物質用触媒構造体の金属微粒子を構成する金属元素(M)に対応する金属成分(例えば、金属イオン)を含有する溶液であればよく、例えば、溶媒に、金属元素(M)を含有する金属塩を溶解させることにより調製できる。このような金属塩としては、例えば、塩化物、水酸化物、酸化物、硫酸塩、硝酸塩等の金属塩が挙げられ、中でも硝酸塩が好ましい。溶媒としては、例えば水、またはアルコール等の有機溶媒、若しくはこれらの混合溶媒等を用いることができる。   The metal-containing solution may be a solution containing a metal component (for example, metal ion) corresponding to the metal element (M) constituting the metal fine particles of the catalyst structure for a volatile organic substance. It can be prepared by dissolving a metal salt containing the element (M). Examples of such metal salts include metal salts such as chlorides, hydroxides, oxides, sulfates, nitrates, etc. Among them, nitrates are preferable. As the solvent, for example, water, an organic solvent such as alcohol, or a mixed solvent thereof can be used.

前駆体材料(A)に金属含有溶液を含浸させる方法は、特に限定されないが、例えば、後述する焼成工程の前に、粉末状の前駆体材料(A)を撹拌しながら、金属含有溶液を複数回に分けて少量ずつ添加することが好ましい。また、前駆体材料(A)の細孔内部に金属含有溶液がより浸入し易くなる観点から、前駆体材料(A)に、金属含有溶液を添加する前に予め、添加剤として界面活性剤を添加しておくことが好ましい。このような添加剤は、前駆体材料(A)の外表面を被覆する働きがあり、その後に添加される金属含有溶液が前駆体材料(A)の外表面に付着することを抑制し、金属含有溶液が前駆体材料(A)の細孔内部により浸入し易くなると考えられる。   The method for impregnating the precursor material (A) with the metal-containing solution is not particularly limited. For example, a plurality of metal-containing solutions are mixed while stirring the powdery precursor material (A) before the firing step described later. It is preferable to add in small portions in portions. Further, from the viewpoint of facilitating the penetration of the metal-containing solution into the pores of the precursor material (A), a surfactant as an additive is added in advance to the precursor material (A) before adding the metal-containing solution. It is preferable to add it. Such an additive has a function of coating the outer surface of the precursor material (A), suppresses the metal-containing solution added thereafter from adhering to the outer surface of the precursor material (A), and the metal It is considered that the contained solution is more likely to enter the pores of the precursor material (A).

このような添加剤としては、例えばポリオキシエチレンオレイルエーテル、ポリオキシエチレンアルキルエーテル、ポリオキシエチレンアルキルフェニルエーテル等の非イオン性界面活性剤が挙げられる。これらの界面活性剤は、分子サイズが大きく前駆体材料(A)の細孔内部には浸入できないため、細孔の内部に付着することは無く、金属含有溶液が細孔内部に浸入することを妨げないと考えられる。非イオン性界面活性剤の添加方法としては、例えば、後述する焼成工程の前に、非イオン性界面活性剤を、前駆体材料(A)に対して50〜500質量%添加するのが好ましい。非イオン性界面活性剤の前駆体材料(A)に対する添加量が50質量%未満であると上記の抑制作用が発現し難く、非イオン性界面活性剤を前駆体材料(A)に対して500質量%よりも多く添加すると粘度が上がりすぎるので好ましくない。よって、非イオン性界面活性剤の前駆体材料(A)に対する添加量を上記範囲内の値とする。   Examples of such additives include nonionic surfactants such as polyoxyethylene oleyl ether, polyoxyethylene alkyl ether, and polyoxyethylene alkylphenyl ether. Since these surfactants have a large molecular size and cannot penetrate into the pores of the precursor material (A), they do not adhere to the inside of the pores, and the metal-containing solution penetrates into the pores. It is thought not to interfere. As a method for adding the nonionic surfactant, for example, it is preferable to add 50 to 500% by mass of the nonionic surfactant with respect to the precursor material (A) before the firing step described later. When the addition amount of the nonionic surfactant to the precursor material (A) is less than 50% by mass, the above-described inhibitory action is hardly exhibited, and the nonionic surfactant is added to the precursor material (A) at 500. Addition of more than% by mass is not preferable because the viscosity increases excessively. Therefore, the addition amount of the nonionic surfactant with respect to the precursor material (A) is set to a value within the above range.

また、前駆体材料(A)に添加する金属含有溶液の添加量は、前駆体材料(A)に含浸させる金属含有溶液中に含まれる金属元素(M)の量(すなわち、前駆体材料(B)に内在させる金属元素(M)の量)を考慮して、適宜調整することが好ましい。例えば、後述する焼成工程の前に、前駆体材料(A)に添加する金属含有溶液の添加量を、前駆体材料(A)に添加する金属含有溶液中に含まれる金属元素(M)に対する、前駆体材料(A)を構成するケイ素(Si)の比(原子数比Si/M)に換算して、10〜1000となるように調整することが好ましく、50〜200となるように調整することがより好ましい。例えば、前駆体材料(A)に金属含有溶液を添加する前に、添加剤として界面活性剤を前駆体材料(A)に添加した場合、前駆体材料(A)に添加する金属含有溶液の添加量を、原子数比Si/Mに換算して50〜200とすることで、金属微粒子の金属元素(M)を、揮発性有機物質用触媒構造体1に対して0.5〜2.5質量%で含有させることができる。前駆体材料(B)の状態で、その細孔内部に存在する金属元素(M)の量は、金属含有溶液の金属濃度や、上記添加剤の有無、その他温度や圧力等の諸条件が同じであれば、前駆体材料(A)に添加する金属含有溶液の添加量に概ね比例する。また、前駆体材料(B)に内在する金属元素(M)の量は、揮発性有機物質用触媒構造体の担体に内在する金属微粒子を構成する金属元素の量と比例関係にある。したがって、前駆体材料(A)に添加する金属含有溶液の添加量を上記範囲に制御することにより、前駆体材料(A)の細孔内部に金属含有溶液を十分に含浸させることができ、ひいては、揮発性有機物質用触媒構造体の担体に内在させる金属微粒子の量を調整することができる。   The amount of the metal-containing solution added to the precursor material (A) is the amount of the metal element (M) contained in the metal-containing solution impregnated in the precursor material (A) (that is, the precursor material (B It is preferable to adjust appropriately in consideration of the amount of the metal element (M) contained in (). For example, before the firing step described later, the addition amount of the metal-containing solution added to the precursor material (A) is the metal element (M) contained in the metal-containing solution added to the precursor material (A), In terms of the ratio of silicon (Si) constituting the precursor material (A) (atomic number ratio Si / M), it is preferably adjusted to be 10 to 1000, and adjusted to be 50 to 200. It is more preferable. For example, when a surfactant is added as an additive to the precursor material (A) before the metal-containing solution is added to the precursor material (A), the addition of the metal-containing solution to be added to the precursor material (A) By converting the amount to 50 to 200 in terms of the atomic ratio Si / M, the metal element (M) of the metal fine particles is 0.5 to 2.5 with respect to the catalyst structure 1 for volatile organic substances. It can be contained by mass%. In the state of the precursor material (B), the amount of the metal element (M) present in the pores is the same as the metal concentration of the metal-containing solution, the presence or absence of the additive, and other conditions such as temperature and pressure. If so, it is roughly proportional to the amount of the metal-containing solution added to the precursor material (A). The amount of the metal element (M) contained in the precursor material (B) is proportional to the amount of the metal element constituting the metal fine particles contained in the carrier of the catalyst structure for volatile organic substances. Therefore, by controlling the amount of the metal-containing solution added to the precursor material (A) within the above range, the metal-containing solution can be sufficiently impregnated inside the pores of the precursor material (A), and thus The amount of fine metal particles contained in the carrier of the catalyst structure for volatile organic substances can be adjusted.

前駆体材料(A)に金属含有溶液を含浸させた後は、必要に応じて、洗浄処理を行ってもよい。洗浄溶液として、水、またはアルコール等の有機溶媒、若しくはこれらの混合溶液を用いることができる。また、前駆体材料(A)に金属含有溶液を含浸させ、必要に応じて洗浄処理を行った後、さらに乾燥処理を施すことが好ましい。乾燥処理としては、一晩程度の自然乾燥や、150℃以下の高温乾燥が挙げられる。なお、金属含有溶液に含まれる水分や、洗浄溶液の水分が、前駆体材料(A)に多く残った状態で、後述の焼成処理を行うと、前駆体材料(A)の規則性メソ細孔物質としての骨格構造が壊れる恐れがあるので、十分に乾燥するのが好ましい。   After impregnating the precursor material (A) with the metal-containing solution, a cleaning treatment may be performed as necessary. As the cleaning solution, water, an organic solvent such as alcohol, or a mixed solution thereof can be used. In addition, it is preferable to impregnate the precursor material (A) with a metal-containing solution and perform a cleaning treatment as necessary, followed by a drying treatment. Examples of the drying treatment include natural drying overnight or high temperature drying at 150 ° C. or lower. In addition, the regular mesopores of the precursor material (A) are obtained by performing the baking treatment described later in a state where a large amount of moisture contained in the metal-containing solution and the moisture of the cleaning solution remain in the precursor material (A). Since the skeletal structure as a substance may be broken, it is preferable to dry it sufficiently.

(ステップS3:焼成工程)
次に、ゼオライト型化合物で構成される多孔質構造の担体を得るための前駆体材料(A)に金属含有溶液が含浸された前駆体材料(B)を焼成して、前駆体材料(C)を得る。
(Step S3: Firing step)
Next, the precursor material (B) obtained by impregnating the precursor material (A) for impregnating the porous material structure composed of the zeolite type compound with the metal-containing solution is calcined to obtain the precursor material (C). Get.

焼成処理は、例えば、空気中で、350〜850℃、2〜30時間の処理条件で行うことが好ましい。このような焼成処理により、規則性メソ細孔物質の孔内に含浸された金属成分が結晶成長して、孔内で金属微粒子が形成される。   The firing treatment is preferably performed, for example, in the air at 350 to 850 ° C. for 2 to 30 hours. By such a baking treatment, the metal component impregnated in the pores of the regular mesoporous material grows and crystal particles are formed in the pores.

(ステップS4:水熱処理工程)
次いで、前駆体材料(C)と構造規定剤とを混合した混合溶液を調製し、前記前駆体材料(B)を焼成して得られた前駆体材料(C)を水熱処理して、揮発性有機物質用触媒構造体を得る。
(Step S4: Hydrothermal treatment process)
Next, a mixed solution in which the precursor material (C) and the structure directing agent are mixed is prepared, and the precursor material (C) obtained by firing the precursor material (B) is hydrothermally treated to be volatile. A catalyst structure for organic substances is obtained.

構造規定剤は、揮発性有機物質用触媒構造体の担体の骨格構造を規定するための鋳型剤であり、例えば界面活性剤を用いることができる。構造規定剤は、揮発性有機物質用触媒構造体の担体の骨格構造に応じて選択することが好ましく、例えばテトラメチルアンモニウムブロミド(TMABr)、テトラエチルアンモニウムブロミド(TEABr)、テトラプロピルアンモニウムブロミド(TPABr)等の界面活性剤が好適である。   The structure directing agent is a templating agent for defining the skeletal structure of the support of the catalyst structure for volatile organic substances, and for example, a surfactant can be used. The structure-directing agent is preferably selected according to the skeletal structure of the support of the catalyst structure for volatile organic substances. For example, tetramethylammonium bromide (TMABr), tetraethylammonium bromide (TEABr), tetrapropylammonium bromide (TPABr) And the like are preferable.

前駆体材料(C)と構造規定剤との混合は、本水熱処理工程時に行ってもよいし、水熱処理工程の前に行ってもよい。また、上記混合溶液の調製方法は、特に限定されず、前駆体材料(C)と、構造規定剤と、溶媒とを同時に混合してもよいし、溶媒に前駆体材料(C)と構造規定剤とをそれぞれ個々の溶液に分散させた状態にした後に、それぞれの分散溶液を混合してもよい。溶媒としては、例えば水、またはアルコール等の有機溶媒、若しくはこれらの混合溶媒等を用いることができる。また、混合溶液は、水熱処理を行う前に、酸または塩基を用いてpHを調整しておくことが好ましい。   Mixing of the precursor material (C) and the structure directing agent may be performed during the main hydrothermal treatment step, or may be performed before the hydrothermal treatment step. Moreover, the preparation method of the said mixed solution is not specifically limited, A precursor material (C), a structure directing agent, and a solvent may be mixed simultaneously, or precursor material (C) and structure prescription | regulation are carried out to a solvent. After each agent is dispersed in each solution, each dispersion solution may be mixed. As the solvent, for example, water, an organic solvent such as alcohol, or a mixed solvent thereof can be used. In addition, the pH of the mixed solution is preferably adjusted using an acid or a base before hydrothermal treatment.

水熱処理は、公知の方法で行うことができ、例えば、密閉容器内で、80〜800℃、5時間〜240時間、0〜2000kPaの処理条件で行うことが好ましい。また、水熱処理は、塩基性雰囲気下で行われることが好ましい。ここでの反応メカニズムは必ずしも明らかではないが、前駆体材料(C)を原料として水熱処理を行うことにより、前駆体材料(C)の規則性メソ細孔物質としての骨格構造は次第に崩れるが、前駆体材料(C)の細孔内部での金属微粒子の位置は概ね維持されたまま、構造規定剤の作用により、揮発性有機物質用触媒構造体の担体としての新たな骨格構造(多孔質構造)が形成される。このようにして得られた揮発性有機物質用触媒構造体は、多孔質構造の担体と、担体に内在する金属微粒子を備え、さらに担体はその多孔質構造により複数の孔が互いに連通した通路を有し、金属微粒子はその少なくとも一部分が担体の通路に存在している。
また、本実施形態では、上記水熱処理工程において、前駆体材料(C)と構造規定剤とを混合した混合溶液を調製して、前駆体材料(C)を水熱処理しているが、これに限らず、前駆体材料(C)と構造規定剤とを混合すること無く、前駆体材料(C)を水熱処理してもよい。
Hydrothermal treatment can be performed by a well-known method, for example, it is preferable to perform in 80-800 degreeC, 5 hours-240 hours, and processing conditions of 0-2000 kPa in an airtight container. The hydrothermal treatment is preferably performed in a basic atmosphere. Although the reaction mechanism here is not necessarily clear, by performing hydrothermal treatment using the precursor material (C) as a raw material, the skeleton structure of the precursor material (C) as a regular mesoporous material gradually collapses. While maintaining the position of the metal fine particles inside the pores of the precursor material (C), a new skeletal structure (porous structure) as a support for the catalyst structure for volatile organic substances by the action of the structure-directing agent. ) Is formed. The catalyst structure for volatile organic substances thus obtained comprises a porous structure carrier and metal fine particles present in the carrier, and the carrier has a passage in which a plurality of holes communicate with each other due to the porous structure. And at least a part of the metal fine particles are present in the passage of the carrier.
In this embodiment, in the hydrothermal treatment step, a mixed solution in which the precursor material (C) and the structure directing agent are mixed is prepared, and the precursor material (C) is hydrothermally treated. Not limited to this, the precursor material (C) may be hydrothermally treated without mixing the precursor material (C) and the structure directing agent.

水熱処理後に得られる沈殿物(揮発性有機物質用触媒構造体)は、回収(例えば、ろ別)後、必要に応じて洗浄、乾燥および焼成することが好ましい。洗浄溶液としては、水、またはアルコール等の有機溶媒、若しくはこれらの混合溶液を用いることができる。乾燥処理としては、一晩程度の自然乾燥や、150℃以下の高温乾燥が挙げられる。なお、沈殿物に水分が多く残った状態で、焼成処理を行うと、揮発性有機物質用触媒構造体の担体としての骨格構造が壊れる恐れがあるので、十分に乾燥するのが好ましい。また、焼成処理は、例えば、空気中で、350〜850℃、2〜30時間の処理条件で行うことができる。このような焼成処理により、揮発性有機物質用触媒構造体に付着していた構造規定剤が焼失する。また、揮発性有機物質用触媒構造体は、使用目的に応じて、回収後の沈殿物を焼成処理することなくそのまま用いることもできる。例えば、揮発性有機物質用触媒構造体の使用する環境が、酸化性雰囲気の高温環境である場合には、使用環境に一定時間晒すことで、構造規定剤は焼失し、焼成処理した場合と同様の揮発性有機物質用触媒構造体が得られるので、そのまま使用することが可能となる。   The precipitate (catalyst structure for a volatile organic substance) obtained after the hydrothermal treatment is preferably washed, dried and calcined as necessary after collection (for example, filtration). As the cleaning solution, water, an organic solvent such as alcohol, or a mixed solution thereof can be used. Examples of the drying treatment include natural drying overnight or high temperature drying at 150 ° C. or lower. In addition, if the calcination treatment is performed in a state where a large amount of moisture remains in the precipitate, the skeleton structure as a support of the catalyst structure for a volatile organic substance may be broken. Therefore, it is preferable to sufficiently dry the precipitate. Moreover, a baking process can be performed on the process conditions of 350-850 degreeC and 2 to 30 hours, for example in the air. By such a calcination treatment, the structure directing agent adhering to the catalyst structure for volatile organic substances is burned out. Moreover, the catalyst structure for volatile organic substances can also be used as it is, without baking the collect | recovered deposit according to the intended purpose. For example, if the environment in which the catalyst structure for volatile organic substances is used is a high-temperature environment in an oxidizing atmosphere, the structure directing agent will be burned out by exposure to the environment for a certain period of time, and it will be the same as when it is fired. Thus, it is possible to use the catalyst structure for a volatile organic substance as it is.

以上説明した製造方法は、前駆体材料(A)に含浸させる金属含有溶液に含まれる金属元素(M)が、酸化され難い金属種(例えば、貴金属)である場合の一例である。   The production method described above is an example in the case where the metal element (M) contained in the metal-containing solution impregnated in the precursor material (A) is a metal species that is difficult to be oxidized (for example, a noble metal).

前駆体材料(A)に含浸させる金属含有溶液中に含まれる金属元素(M)が、酸化され易い金属種(例えば、Fe、Co、Cu等)である場合には、上記水熱処理工程後に、水熱処理された前駆体材料(C)に還元処理を行うことが好ましい。金属含有溶液中に含まれる金属元素(M)が、酸化され易い金属種である場合、含浸処理(ステップS2)の後の工程(ステップS3〜S4)における熱処理により、金属成分が酸化されてしまう。そのため、水熱処理工程(ステップS4)で形成される担体には、金属酸化物微粒子が内在することになる。そのため、担体に金属微粒子が内在する揮発性有機物質用触媒構造体を得るためには、上記水熱処理後に、回収した沈殿物を焼成処理し、さらに水素ガス等の還元ガス雰囲気下で還元処理することが望ましい(ステップS5:還元処理工程)。還元処理を行うことにより、担体に内在する金属酸化物微粒子が還元され、金属酸化物微粒子を構成する金属元素(M)に対応する金属微粒子が形成される。その結果、担体に金属微粒子が内在する揮発性有機物質用触媒構造体が得られる。なお、このような還元処理は、必要に応じて行えばよく、例えば、揮発性有機物質用触媒構造体を使用する環境が、還元雰囲気である場合には、使用環境に一定時間晒すことで、金属酸化物微粒子は還元されるため、還元処理した場合と同様の揮発性有機物質用触媒構造体が得られるので、担体に酸化物微粒子が内在した状態でそのまま使用することが可能となる。   When the metal element (M) contained in the metal-containing solution impregnated in the precursor material (A) is a metal species that is easily oxidized (eg, Fe, Co, Cu, etc.), after the hydrothermal treatment step, It is preferable to perform a reduction treatment on the hydrothermally treated precursor material (C). When the metal element (M) contained in the metal-containing solution is an easily oxidized metal species, the metal component is oxidized by the heat treatment in the steps (steps S3 to S4) after the impregnation treatment (step S2). . Therefore, the metal oxide fine particles are inherent in the support formed in the hydrothermal treatment step (step S4). Therefore, in order to obtain a catalyst structure for volatile organic substances in which fine metal particles are present in the carrier, the recovered precipitate is calcined after the hydrothermal treatment, and further reduced under a reducing gas atmosphere such as hydrogen gas. It is desirable (step S5: reduction process). By performing the reduction treatment, the metal oxide fine particles present in the carrier are reduced, and metal fine particles corresponding to the metal element (M) constituting the metal oxide fine particles are formed. As a result, a catalyst structure for a volatile organic substance in which metal fine particles are inherently present in the carrier is obtained. In addition, such a reduction treatment may be performed as necessary. For example, when the environment in which the catalyst structure for volatile organic substances is used is a reducing atmosphere, by exposing it to the use environment for a certain period of time, Since the metal oxide fine particles are reduced, the same volatile organic substance catalyst structure as that obtained by the reduction treatment can be obtained, so that the oxide fine particles can be used as they are in the carrier.

[揮発性有機物質用触媒構造体1の変形例]
図4は、図1の揮発性有機物質用触媒構造体1の変形例を示す模式図である。
図1の揮発性有機物質用触媒構造体1は、担体10と、担体10に内在する金属微粒子20とを備える場合を示しているが、この構成だけには限定されず、例えば、図4に示すように、揮発性有機物質用触媒構造体2が、担体10の外表面10aに保持された、揮発性有機物質酸化触媒物質である他の金属微粒子30を更に備えていてもよい。
[Modification of Catalyst Structure 1 for Volatile Organic Substances]
FIG. 4 is a schematic view showing a modification of the volatile organic substance catalyst structure 1 of FIG.
The volatile organic substance catalyst structure 1 of FIG. 1 shows a case where the support 10 and the metal fine particles 20 existing in the support 10 are provided. However, the present invention is not limited to this configuration. For example, FIG. As shown, the catalyst structure 2 for volatile organic substances may further include other metal fine particles 30 that are volatile organic substance oxidation catalyst substances held on the outer surface 10 a of the carrier 10.

この他の金属微粒子30は、一又は複数の触媒能を発揮する物質である。他の金属微粒子30が有する触媒能は、金属微粒子20が有する触媒能と同一であってもよいし、異なっていてもよい。また、金属微粒子20,30の双方が同一の触媒能を有する物質である場合、他の金属微粒子30の材料は、金属微粒子20の材料と同一であってもよいし、異なっていてもよい。本構成によれば、揮発性有機物質用触媒構造体2に保持された揮発性有機物質酸化触媒物質の含有量を増大することができ、揮発性有機物質酸化触媒物質の触媒活性を更に促進することができる。   The other metal fine particles 30 are substances that exhibit one or more catalytic ability. The catalytic ability of the other metal fine particles 30 may be the same as or different from the catalytic ability of the metal fine particles 20. In addition, when both of the metal fine particles 20 and 30 are substances having the same catalytic ability, the material of the other metal fine particles 30 may be the same as or different from the material of the metal fine particles 20. According to this configuration, it is possible to increase the content of the volatile organic material oxidation catalyst material held in the volatile organic material catalyst structure 2, and further promote the catalytic activity of the volatile organic material oxidation catalyst material. be able to.

この場合、担体10に内在する金属微粒子20の含有量は、担体10の外表面10aに保持された他の金属微粒子30の含有量よりも多いことが好ましい。これにより、担体10の内部に保持された金属微粒子20による触媒能が支配的となり、安定的に揮発性有機物質酸化触媒物質の触媒能が発揮される。   In this case, the content of the metal fine particles 20 inherent in the carrier 10 is preferably larger than the content of the other metal fine particles 30 held on the outer surface 10 a of the carrier 10. As a result, the catalytic ability of the metal fine particles 20 held inside the carrier 10 becomes dominant, and the catalytic ability of the volatile organic substance oxidation catalyst substance is stably exhibited.

以上、本発明の実施形態に係る揮発性有機物質用触媒構造体について述べたが、本発明は上記実施形態に限定されるものではなく、本発明の技術思想に基づいて各種の変形および変更が可能である。   As mentioned above, although the catalyst structure for volatile organic substances according to the embodiment of the present invention has been described, the present invention is not limited to the above embodiment, and various modifications and changes can be made based on the technical idea of the present invention. Is possible.

(実施例1〜384)
[前駆体材料(A)の合成]
シリカ剤(テトラエトキシシラン(TEOS)、和光純薬工業株式会社製)と、鋳型剤としての界面活性剤とを混合した混合水溶液を作製し、適宜pH調整を行い、密閉容器内で、80〜350℃、100時間、水熱処理を行った。その後、生成した沈殿物をろ別し、水およびエタノールで洗浄し、さらに600℃、24時間、空気中で焼成して 、 表1〜8に示される種類および孔径の前駆体材料(A)を得た。なお、界面活性剤は、前駆体材料(A)の種類に応じて(「前駆体材料(A)の種類:界面活性剤」)以下のものを用いた。
・MCM−41:ヘキサデシルトリメチルアンモニウムブロミド(CTAB)(和光純薬工業株式会社製)
・SBA−1:Pluronic P123(BASF社製)
(Examples 1 to 384)
[Synthesis of Precursor Material (A)]
A mixed aqueous solution in which a silica agent (tetraethoxysilane (TEOS), manufactured by Wako Pure Chemical Industries, Ltd.) and a surfactant as a templating agent was mixed was prepared, pH was adjusted as appropriate, and 80 to 80 in a sealed container. Hydrothermal treatment was performed at 350 ° C. for 100 hours. Thereafter, the produced precipitate is filtered off, washed with water and ethanol, and further calcined in air at 600 ° C. for 24 hours to obtain precursor materials (A) of the types and pore sizes shown in Tables 1-8. Obtained. The following surfactants were used according to the type of the precursor material (A) (“type of precursor material (A): surfactant”).
MCM-41: hexadecyltrimethylammonium bromide (CTAB) (manufactured by Wako Pure Chemical Industries, Ltd.)
・ SBA-1: Pluronic P123 (manufactured by BASF)

[前駆体材料(B)および(C)の作製]
次に、表1〜8に示される種類の金属微粒子を構成する金属元素(M)に応じて、該金属元素(M)を含有する金属塩を、水に溶解させて、金属含有水溶液を調製した。なお、金属塩は、金属微粒子の種類に応じて(「金属微粒子:金属塩」)以下のものを用いた。
・Pt:塩化白金酸六水和物(和光純薬工業株式会社製)
・Pd:硝酸パラジウム(II)水和物(和光純薬工業株式会社製)
・Ru:塩化ルテニウム(III)n水和物(和光純薬工業株式会社製)
・Rh:硝酸ロジウム(III)(n水和物)(和光純薬工業株式会社製)
[Preparation of precursor materials (B) and (C)]
Next, a metal salt containing the metal element (M) is dissolved in water according to the metal element (M) constituting the type of metal fine particles shown in Tables 1 to 8 to prepare a metal-containing aqueous solution. did. The following metal salts were used according to the type of metal fine particles (“metal fine particles: metal salt”).
Pt: Chloroplatinic acid hexahydrate (manufactured by Wako Pure Chemical Industries, Ltd.)
Pd: palladium nitrate (II) hydrate (manufactured by Wako Pure Chemical Industries, Ltd.)
Ru: Ruthenium (III) chloride n hydrate (Wako Pure Chemical Industries, Ltd.)
Rh: rhodium nitrate (III) (n hydrate) (manufactured by Wako Pure Chemical Industries, Ltd.)

次に、粉末状の前駆体材料(A)に、金属含有水溶液を複数回に分けて少量ずつ添加し、室温(20℃±10℃)で12時間以上乾燥させて、前駆体材料(B)を得た。   Next, the metal-containing aqueous solution is added to the powdery precursor material (A) in small portions in small portions, and dried at room temperature (20 ° C. ± 10 ° C.) for 12 hours or more to obtain the precursor material (B). Got.

なお、表1〜8に示す添加剤の有無の条件が「有り」の場合は、金属含有水溶液を添加する前の前駆体材料(A)に対して、添加剤としてのポリオキシエチレン(15)オレイルエーテル(NIKKOL BO−15V、日光ケミカルズ株式会社製)の水溶液を添加する前処理を行い、その後、上記のように金属含有水溶液を添加した。なお、添加剤の有無の条件で「無し」の場合については、上記のような添加剤による前処理は行っていない。   In addition, when the condition of the presence or absence of the additive shown in Tables 1 to 8 is “Yes”, polyoxyethylene (15) as an additive with respect to the precursor material (A) before adding the metal-containing aqueous solution A pretreatment of adding an aqueous solution of oleyl ether (NIKKOL BO-15V, manufactured by Nikko Chemicals Co., Ltd.) was performed, and then the metal-containing aqueous solution was added as described above. In the case of “None” in the presence or absence of the additive, the pretreatment with the additive as described above is not performed.

また、前駆体材料(A)に添加する金属含有水溶液の添加量は、該金属含有水溶液中に含まれる金属元素(M)に対する、前駆体材料(A)を構成するケイ素(Si)の比(原子数比Si/M)に換算したときの数値が、表1〜8の値になるように調整した。   Moreover, the addition amount of the metal-containing aqueous solution added to the precursor material (A) is the ratio of silicon (Si) constituting the precursor material (A) to the metal element (M) contained in the metal-containing aqueous solution ( The numerical values when converted to the atomic ratio (Si / M) were adjusted to the values shown in Tables 1-8.

次に、上記のようにして得られた金属含有水溶液を含浸させた前駆体材料(B)を、600℃、24時間、空気中で焼成して、前駆体材料(C)を得た。   Next, the precursor material (B) impregnated with the metal-containing aqueous solution obtained as described above was baked in air at 600 ° C. for 24 hours to obtain a precursor material (C).

上記のようにして得られた前駆体材料(C)と、表1〜8に示す構造規定剤とを混合して混合水溶液を作製し、密閉容器内で、80〜350℃、表1〜8に示すpHおよび時間の条件で、水熱処理を行った。その後、生成した沈殿物をろ別し、水洗し、100℃で12時間以上乾燥させ、さらに600℃、24時間、空気中で焼成した。その後、焼成物を回収し、水素ガスの流入下で、400℃、350分間、還元処理して、表1〜8に示す担体と触媒物質としての金属微粒子とを有する触媒構造体を得た(実施例1〜384)。   The precursor material (C) obtained as described above and the structure directing agent shown in Tables 1 to 8 are mixed to prepare a mixed aqueous solution, and 80 to 350 ° C. and Tables 1 to 8 in a sealed container. Hydrothermal treatment was performed under the conditions of pH and time shown in FIG. Thereafter, the produced precipitate was filtered off, washed with water, dried at 100 ° C. for 12 hours or more, and further calcined in air at 600 ° C. for 24 hours. Thereafter, the fired product was recovered and subjected to reduction treatment at 400 ° C. for 350 minutes under inflow of hydrogen gas to obtain a catalyst structure having a carrier and metal fine particles as a catalyst material shown in Tables 1 to 8 ( Examples 1-384).

(比較例1)
比較例1では、MFI型シリカライトに平均粒径50nm以下の酸化コバルト粉末(II,III)(シグマ アルドリッチ ジャパン合同会社製)を混合し、実施例と同様にして水素還元処理を行って、担体としてのシリカライトの外表面に、触媒物質としてコバルト微粒子を付着させた触媒構造体を得た。MFI型シリカライトは、金属を添加する工程以外は、実施例52〜57と同様の方法で合成した。
(Comparative Example 1)
In Comparative Example 1, cobalt oxide powder (II, III) (manufactured by Sigma Aldrich Japan G.K.) having an average particle size of 50 nm or less was mixed with MFI type silicalite and subjected to hydrogen reduction treatment in the same manner as in Example, As a result, a catalyst structure in which cobalt fine particles were adhered as a catalyst material to the outer surface of silicalite was obtained. MFI type silicalite was synthesized in the same manner as in Examples 52 to 57 except for the step of adding metal.

(比較例2)
比較例2では、コバルト微粒子を付着させる工程を省略したこと以外は、比較例1と同様の方法にてMFI型シリカライトを合成した。
(Comparative Example 2)
In Comparative Example 2, MFI type silicalite was synthesized by the same method as Comparative Example 1 except that the step of attaching cobalt fine particles was omitted.

[評価]
担体と触媒物質とを備える上記実施例の触媒構造体および比較例のシリカライトについて、以下に示す条件で、各種特性評価を行った。
[Evaluation]
Various characteristics evaluation was performed on the catalyst structures of the above-mentioned examples including a support and a catalyst substance and silicalites of the comparative examples under the following conditions.

[A]断面観察
担体と触媒物質とを備える上記実施例の触媒構造体および比較例1のシリカライトについて、粉砕法にて観察試料を作製し、透過電子顕微鏡(TEM)(TITAN G2、FEI社製)を用いて、断面観察を行った。
その結果、上記実施例の触媒構造体では、シリカライトまたはゼオライトからなる担体の内部に触媒物質が内在し、保持されていることが確認された。一方、比較例1のシリカライトでは、触媒物質が担体の外表面に付着しているのみで、担体の内部には存在していなかった。
また、上記実施例のうち金属が鉄微粒子(Fe)である触媒構造体について、FIB(集束イオンビーム)加工により断面を切り出し、SEM(SU8020、日立ハイテクノロジーズ社製)、EDX(X−Max、堀場製作所製)を用いて断面元素分析を行った。その結果、担体内部からFe元素が検出された。
上記TEMとSEM/EDXによる断面観察の結果から、担体内部に鉄微粒子が存在していることが確認された。
[A] Cross-sectional observation About the catalyst structure of the said Example provided with a support | carrier and a catalyst substance, and the silicalite of the comparative example 1, an observation sample was produced with the grinding | pulverization method, and a transmission electron microscope (TEM) (TITA G2, FEI company) Were used for cross-sectional observation.
As a result, in the catalyst structures of the above examples, it was confirmed that the catalyst substance was present and retained inside the support made of silicalite or zeolite. On the other hand, in the silicalite of Comparative Example 1, the catalyst substance was only attached to the outer surface of the carrier and was not present inside the carrier.
Moreover, about the catalyst structure whose metal is iron fine particles (Fe) among the said Example, a cross section is cut out by FIB (focused ion beam) processing, SEM (SU8020, Hitachi High-Technologies company make), EDX (X-Max, Cross-sectional elemental analysis was performed using HORIBA, Ltd. As a result, Fe element was detected from inside the support.
From the results of cross-sectional observation using the TEM and SEM / EDX, it was confirmed that iron fine particles were present inside the carrier.

[B]担体の通路の平均内径および触媒物質の平均粒径
上記評価[A]で行った断面観察により撮影したTEM画像にて、担体の通路を、任意に500個選択し、それぞれの長径および短径を測定し、その平均値からそれぞれの内径を算出し(N=500)、さらに内径の平均値を求めて、担体の通路の平均内径Dとした。また、触媒物質についても同様に、上記TEM画像から、触媒物質を、任意に500個選択し、それぞれの粒径を測定して(N=500)、その平均値を求めて、触媒物質の平均粒径Dとした。結果を表1〜8に示す。
また、触媒物質の平均粒径及び分散状態を確認するため、SAXS(小角X線散乱)を用いて分析した。SAXSによる測定は、Spring−8のビームラインBL19B2を用いて行った。得られたSAXSデータは、Guinier近似法により球形モデルでフィッティングを行い、粒径を算出した。粒径は、金属が鉄微粒子である触媒構造体について測定した。また、比較対象として、市販品である鉄微粒子(Wako製)をSEMにて観察、測定した。
この結果、市販品では粒径約50nm〜400nmの範囲で様々なサイズの酸化鉄微粒子がランダムに存在しているのに対し、TEM画像から求めた平均粒径が1.2nm〜2.0nmの各実施例の触媒構造体では、SAXSの測定結果においても粒径が10nm以下の散乱ピークが検出された。SAXSの測定結果とSEM/EDXによる断面の測定結果から、担体内部に、粒径10nm以下の触媒物質が、粒径が揃いかつ非常に高い分散状態で存在していることが分かった。
[B] Average inner diameter of carrier passage and average particle diameter of catalyst substance In the TEM image taken by cross-sectional observation performed in the above evaluation [A], arbitrarily select 500 passages of the carrier, The short diameter was measured, the inner diameter was calculated from the average value (N = 500), and the average inner diameter was further calculated as the average inner diameter DF of the carrier passage. Similarly, for the catalyst material, 500 catalyst materials are arbitrarily selected from the TEM image, each particle size is measured (N = 500), an average value thereof is obtained, and the average of the catalyst materials is determined. I was having a particle diameter D C. The results are shown in Tables 1-8.
Moreover, in order to confirm the average particle diameter and dispersion state of a catalyst substance, it analyzed using SAXS (small angle X-ray scattering). The SAXS measurement was performed using Spring-8 beam line BL19B2. The obtained SAXS data was fitted with a spherical model by the Guinier approximation method, and the particle size was calculated. The particle size was measured for a catalyst structure in which the metal is iron fine particles. In addition, as a comparison object, commercially available iron fine particles (manufactured by Wako) were observed and measured with an SEM.
As a result, in the commercial product, iron oxide fine particles of various sizes are randomly present in the particle size range of about 50 nm to 400 nm, whereas the average particle size obtained from the TEM image is 1.2 nm to 2.0 nm. In the catalyst structure of each Example, a scattering peak having a particle size of 10 nm or less was detected in the SAXS measurement results. From the SAXS measurement result and the cross-sectional measurement result by SEM / EDX, it was found that a catalyst substance having a particle size of 10 nm or less was present in the carrier in a very dispersed state with a uniform particle size.

[C]金属含有溶液の添加量と担体内部に包接された金属量との関係
原子数比Si/M=50,100,200,1000(M=Co、Ni、Fe、Cu)の添加量で、金属微粒子を担体内部に包接させた触媒構造体を作製し、その後、上記添加量で作製された触媒構造体の担体内部に包接された金属量(質量%)を測定した。尚、本測定において原子数比Si/M=100,200,1000の触媒構造体は、それぞれ実施例1〜384のうちの原子数比Si/M=100,200,1000の触媒構造体と同様の方法で金属含有溶液の添加量を調整して作製し、原子数比Si/M=50の触媒構造体は、金属含有溶液の添加量を異ならせたこと以外は、原子数比Si/M=100,200,1000の触媒構造体と同様の方法で作製した。
金属量の定量は、ICP(高周波誘導結合プラズマ)単体か、或いはICPとXRF(蛍光X線分析)を組み合わせて行った。XRF(エネルギー分散型蛍光X線分析装置「SEA1200VX」、エスエスアイ・ナノテクノロジー社製)は、真空雰囲気、加速電圧15kV(Crフィルター使用)或いは加速電圧50kV(Pbフィルター使用)の条件で行った。
XRFは、金属の存在量を蛍光強度で算出する方法であり、XRF単体では定量値(質量%換算)を算出できない。そこで、Si/M=100で金属を添加した触媒構造体の金属量は、ICP分析により定量し、Si/M=50および100未満で金属を添加した触媒構造体の金属量は、XRF測定結果とICP測定結果を元に算出した。
この結果、少なくとも原子数比Si/Mが50〜1000の範囲内で、金属含有溶液の添加量の増加に伴って、触媒構造体に包接された金属量が増大していることが確認された。
[C] Relationship between the addition amount of the metal-containing solution and the amount of metal included in the support The addition amount of the atomic ratio Si / M = 50, 100, 200, 1000 (M = Co, Ni, Fe, Cu) Then, a catalyst structure in which metal fine particles were included in the inside of the support was prepared, and then the amount of metal (mass%) included in the support of the catalyst structure prepared in the above addition amount was measured. In this measurement, the catalyst structure with atomic number ratio Si / M = 100, 200, 1000 is the same as the catalyst structure with atomic number ratio Si / M = 100, 200, 1000 in Examples 1 to 384, respectively. The catalyst structure having an atomic ratio Si / M = 50 was prepared by adjusting the amount of addition of the metal-containing solution by the method described above, except that the amount of addition of the metal-containing solution was changed. = 100, 200, 1000 It was produced by the same method as the catalyst structure.
The amount of metal was determined by using ICP (high frequency inductively coupled plasma) alone or a combination of ICP and XRF (fluorescence X-ray analysis). XRF (energy dispersive X-ray fluorescence spectrometer “SEA1200VX”, manufactured by SSI Nanotechnology Inc.) was performed under the conditions of a vacuum atmosphere, an acceleration voltage of 15 kV (using a Cr filter), or an acceleration voltage of 50 kV (using a Pb filter).
XRF is a method of calculating the abundance of a metal by fluorescence intensity, and a quantitative value (mass% conversion) cannot be calculated with XRF alone. Therefore, the amount of metal in the catalyst structure added with metal at Si / M = 100 was quantified by ICP analysis, and the amount of metal in the catalyst structure added with metal at Si / M = 50 and less than 100 was determined by XRF measurement results. And calculated based on the ICP measurement results.
As a result, it was confirmed that the amount of metal included in the catalyst structure increased as the amount of the metal-containing solution added increased at least in the atomic ratio Si / M in the range of 50 to 1000. It was.

[D]性能評価
担体と触媒物質とを備える上記実施例の触媒構造体および比較例のシリカライトについて、触媒物質がもつ触媒能を評価した。結果を表1〜8に示す。
[D] Performance Evaluation The catalytic ability of the catalyst material was evaluated for the catalyst structures of the above examples and the silicalite of the comparative example provided with a support and a catalyst material. The results are shown in Tables 1-8.

(1)触媒活性
触媒活性は、以下の条件で評価した。
まず、触媒構造体を、常圧流通式反応装置に0.2g充填し、窒素ガス(N)をキャリアガス(5ml/min)とし、400℃、2時間、トルエン(VOCのモデル物質)ガスの分解反応を行った。
反応終了後に、回収した生成ガスおよび生成液を、ガスクロマトグラフィー質量分析法(GC/MS)により成分分析した。なお、生成ガスの分析装置には、TRACE 13 10GC(サーモフィッシャーサイエンティフィック株式会社製、検出器:熱伝導度検出器)を用いた。
さらに、上記成分分析の結果に基づき、トルエンよりも分子量が小さい化合物(具体的には、CO、CO、HCOH等)の収率(mol%)を求めた。上記化合物の収率は、反応開始前のトルエンの物質量(mol)に対する、生成ガス中に含まれるトルエンよりも分子量が小さい化合物の物質量の総量(mol)の百分率(mol%)として算出した。
本実施例では、生成ガス中に含まれるトルエンよりも分子量が小さい化合物の収率が、80mol%以上である場合を触媒活性(分解能)が優れていると判定して「◎」、50mol%以上80mol%未満である場合を触媒活性が良好であると判定して「○」、20mol%以上50mol%未満である場合を触媒活性が良好ではないものの合格レベル(可)でありと判定して「△」、そして20mol%未満である場合を触媒活性が劣る(不可)と判定して「×」とした。
(1) Catalytic activity The catalytic activity was evaluated under the following conditions.
First, 0.2 g of the catalyst structure is charged into an atmospheric pressure flow reactor, nitrogen gas (N 2 ) is used as a carrier gas (5 ml / min), and a toluene (model material of VOC) gas at 400 ° C. for 2 hours. The decomposition reaction of was carried out.
After completion of the reaction, the collected product gas and product liquid were subjected to component analysis by gas chromatography mass spectrometry (GC / MS). Note that TRACE 13 10GC (manufactured by Thermo Fisher Scientific Co., Ltd., detector: thermal conductivity detector) was used as a product gas analyzer.
Furthermore, based on the results of the component analysis, the yield (mol%) of a compound having a smaller molecular weight than toluene (specifically, CO 2 , CO, HCOH, etc.) was determined. The yield of the above compound was calculated as a percentage (mol%) of the total amount (mol) of the compound amount having a molecular weight smaller than that of toluene contained in the product gas with respect to the amount (mol) of toluene before starting the reaction. .
In this example, when the yield of the compound having a molecular weight smaller than that of toluene contained in the product gas is 80 mol% or more, it is determined that the catalytic activity (resolution) is excellent, “◎”, 50 mol% or more. When it is less than 80 mol%, it is determined that the catalyst activity is good, and “◯”, and when it is 20 mol% or more and less than 50 mol%, it is determined that the catalyst activity is not good but the pass level is acceptable. The case where “Δ” was less than 20 mol% was judged to be inferior in catalyst activity (impossible), and “x” was assigned.

(2)耐久性(寿命)
耐久性は、以下の条件で評価した。
まず、上記評価(1)で使用した触媒構造体を回収し、650℃で、12時間加熱して、加熱後の触媒構造体を作製した。次に、得られた加熱後の触媒構造体を用いて、上記評価(1)と同様の方法により、トルエン(VOCのモデル物質)ガスの分解反応を行い、さらに上記評価(1)と同様の方法で、生成ガスの成分分析を行った。
得られた分析結果に基づき、上記評価(1)と同様の方法で、トルエンよりも分子量が小さい化合物の収率(mol%)を求めた。さらに、加熱前の触媒構造体による上記化合物の収率(上記評価(1)で求めた収率)と比較して、加熱後の触媒構造体による上記化合物の収率が、どの程度維持されているかを比較した。具体的には、加熱前の触媒構造体による上記化合物の収率(上記評価(1)で求めた収率)に対する、上記加熱後の触媒構造体による上記化合物の収率(本評価(2)で求めた収率)の百分率(%)を算出した。
本実施例では、加熱後の触媒構造体による上記化合物の収率(本評価(2)で求めた収率)が、加熱前の触媒構造体による上記化合物の収率(上記評価(1)で求めた収率)に比べて、80%以上維持されている場合を耐久性(耐熱性)が優れていると判定して「◎」、50%以上80%未満維持されている場合を耐久性(耐熱性)が良好であると判定して「○」、20%以上50%未満維持されている場合を耐久性(耐熱性)が良好ではないものの合格レベル(可)でありと判定して「△」、そして20%未満に低下している場合を耐久性(耐熱性)が劣る(不可)と判定して「×」とした。
(2) Durability (life)
The durability was evaluated under the following conditions.
First, the catalyst structure used in the evaluation (1) was collected and heated at 650 ° C. for 12 hours to produce a heated catalyst structure. Next, by using the obtained catalyst structure after heating, a decomposition reaction of toluene (model material of VOC) gas is performed by the same method as in the above evaluation (1), and the same as in the above evaluation (1). The component analysis of the product gas was performed by this method.
Based on the obtained analysis results, the yield (mol%) of a compound having a molecular weight smaller than that of toluene was determined in the same manner as in the evaluation (1). Furthermore, compared to the yield of the compound by the catalyst structure before heating (the yield obtained in the evaluation (1) above), how much the yield of the compound by the catalyst structure after heating is maintained. Compared. Specifically, the yield of the compound by the catalyst structure after the heating (the present evaluation (2)) relative to the yield of the compound by the catalyst structure before the heating (the yield obtained in the evaluation (1)). The percentage (%) of the yield obtained in step 1) was calculated.
In this example, the yield of the above compound by the catalyst structure after heating (the yield determined in this evaluation (2)) is the yield of the above compound by the catalyst structure before heating (in the above evaluation (1)). It is judged that the durability (heat resistance) is excellent when it is maintained at 80% or more compared to the yield (determined yield), and the durability when it is maintained at 50% or more and less than 80%. Judgment is good (heat resistance), “○”, and when 20% or more and less than 50% are maintained, the durability (heat resistance) is not good, but it is judged as acceptable level (possible) A case where “△” and a decrease to less than 20% was judged that the durability (heat resistance) was inferior (impossible), and “X” was assigned.

比較例1〜2についても、上記評価(1)および(2)と同様の性能評価を行った。尚、比較例2は、担体そのものであり、触媒物質は有していない。そのため、上記性能評価では、触媒構造体に替えて、比較例2の担体のみを充填した。結果を表8に示す。   About Comparative Examples 1-2, the same performance evaluation as said evaluation (1) and (2) was performed. In addition, the comparative example 2 is a support | carrier itself, and does not have a catalyst substance. Therefore, in the performance evaluation, only the support of Comparative Example 2 was filled instead of the catalyst structure. The results are shown in Table 8.

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表1〜8から明らかなように、断面観察により担体の内部に触媒物質が存在していることが確認された触媒構造体(実施例1〜384)は、単に触媒物質が担体の外表面に付着しているだけの触媒構造体(比較例1)または触媒物質を何ら有していない担体そのもの(比較例2)と比較して、トルエンの分解反応において優れた触媒活性を示し、触媒としての耐久性にも優れていることが分かった。   As is clear from Tables 1 to 8, the catalyst structures (Examples 1 to 384) in which the catalyst substance was confirmed to be present inside the support by cross-sectional observation were simply put on the outer surface of the support. Compared with the catalyst structure (Comparative Example 1) that is only adhered or the carrier itself without any catalytic substance (Comparative Example 2), it exhibits excellent catalytic activity in the decomposition reaction of toluene, It was found to be excellent in durability.

一方、触媒物質を何ら有していない比較例2の担体そのものは、トルエンの分解反応において触媒活性は殆ど示さず、実施例1〜384の触媒構造体と比較して、触媒活性および耐久性の双方が劣っていた。   On the other hand, the support itself of Comparative Example 2, which does not have any catalyst substance, shows almost no catalytic activity in the decomposition reaction of toluene. Compared with the catalyst structures of Examples 1 to 384, the carrier activity and durability of the support itself. Both were inferior.

また、担体の外表面にのみ触媒物質を付着させた比較例1の触媒構造体は、触媒物質を何ら有していない比較例2の担体そのものと比較して、トルエンの分解反応における触媒活性は改善されるものの、実施例1〜384の触媒構造体に比べて、触媒としての耐久性は劣っていた。   In addition, the catalytic structure of Comparative Example 1 in which the catalytic material is attached only to the outer surface of the carrier has a catalytic activity in the decomposition reaction of toluene as compared with the carrier of Comparative Example 2 that does not have any catalytic material. Although improved, the durability as a catalyst was inferior to the catalyst structures of Examples 1 to 384.

1 揮発性有機物質用触媒構造体
10 担体
10a 外表面
11 通路
11a 孔
12 拡径部
20 金属微粒子
30 金属微粒子
平均粒径
平均内径
内径
1 volatile organic material for the catalytic structure 10 support 10a outer surface 11 passages 11a hole 12 enlarged diameter portion 20 the metal particles 30 metal fine particles D C average particle diameter D F average inner diameter D E inner diameter

Claims (22)

ゼオライト型化合物で構成される多孔質構造の担体と、
前記担体に内在する少なくとも1つの、金属からなる揮発性有機物質酸化触媒と、
を備え、
前記担体が、互いに連通する通路を有し、
前記揮発性有機物質酸化触媒が、前記担体の少なくとも前記通路に存在していることを特徴とする揮発性有機物質用触媒構造体。
A porous structure carrier composed of a zeolite-type compound;
At least one volatile organic substance oxidation catalyst comprising a metal inherent in the carrier;
With
The carrier has passages communicating with each other;
A catalyst structure for a volatile organic substance, wherein the volatile organic substance oxidation catalyst is present in at least the passage of the carrier.
前記通路は、前記ゼオライト型化合物の骨格構造によって画定される一次元孔、二次元孔及び三次元孔のうちのいずれかと、前記一次元孔、前記二次元孔及び前記三次元孔のうちのいずれとも異なる拡径部を有し、かつ
前記揮発性有機物質酸化触媒が、少なくとも前記拡径部に存在していることを特徴とする、請求項1に記載の揮発性有機物質用触媒構造体。
The passage is any one of a one-dimensional hole, a two-dimensional hole, and a three-dimensional hole defined by a skeleton structure of the zeolite-type compound, and any one of the one-dimensional hole, the two-dimensional hole, and the three-dimensional hole. 2. The catalyst structure for volatile organic substances according to claim 1, wherein the volatile organic substance oxidation catalyst is present at least in the enlarged diameter part.
前記拡径部は、前記一次元孔、前記二次元孔及び前記三次元孔のうちのいずれかを構成する複数の孔同士を連通している、請求項2に記載の揮発性有機物質用触媒構造体。   The volatile organic substance catalyst according to claim 2, wherein the enlarged-diameter portion communicates a plurality of holes constituting any one of the one-dimensional hole, the two-dimensional hole, and the three-dimensional hole. Structure. 前記揮発性有機物質酸化触媒が、金属微粒子であることを特徴とする、請求項2又は3に記載の揮発性有機物質用触媒構造体。   The catalyst structure for volatile organic substances according to claim 2 or 3, wherein the volatile organic substance oxidation catalyst is metal fine particles. 前記金属微粒子の平均粒径が、前記通路の平均内径よりも大きく、且つ前記拡径部の内径以下であることを特徴とする、請求項4に記載の揮発性有機物質用触媒構造体。   5. The catalyst structure for volatile organic substances according to claim 4, wherein an average particle diameter of the metal fine particles is larger than an average inner diameter of the passage and is equal to or smaller than an inner diameter of the enlarged diameter portion. 前記金属微粒子の金属元素(M)が、前記揮発性有機物質用触媒構造体に対して0.5〜2.5質量%で含有されていることを特徴とする、請求項5に記載の揮発性有機物質用触媒構造体。   The volatilization according to claim 5, wherein the metal element (M) of the metal fine particles is contained in an amount of 0.5 to 2.5% by mass with respect to the catalyst structure for a volatile organic substance. Catalyst structure for organic substances. 前記金属微粒子の平均粒径が、0.08nm〜30nmであることを特徴とする、請求項4〜6のいずれか1項に記載の揮発性有機物質用触媒構造体。   7. The catalyst structure for a volatile organic substance according to claim 4, wherein an average particle diameter of the metal fine particles is 0.08 nm to 30 nm. 前記金属微粒子の平均粒径が、0.4nm〜11.0nmであることを特徴とする、請求項7に記載の揮発性有機物質用触媒構造体。   8. The catalyst structure for volatile organic substances according to claim 7, wherein an average particle diameter of the metal fine particles is 0.4 nm to 11.0 nm. 前記通路の平均内径に対する前記金属微粒子の平均粒径の割合が、0.05〜300であることを特徴とする、請求項4〜8のいずれか1項に記載の揮発性有機物質用触媒構造体。   The catalyst structure for volatile organic substances according to any one of claims 4 to 8, wherein a ratio of an average particle diameter of the metal fine particles to an average inner diameter of the passage is 0.05 to 300. body. 前記通路の平均内径に対する前記金属微粒子の平均粒径の割合が、0.1〜30であることを特徴とする、請求項9に記載の揮発性有機物質用触媒構造体。   10. The catalyst structure for volatile organic substances according to claim 9, wherein a ratio of an average particle diameter of the metal fine particles to an average inner diameter of the passage is 0.1 to 30. 11. 前記通路の平均内径に対する前記金属微粒子の平均粒径の割合が、1.4〜3.6であることを特徴とする、請求項10に記載の揮発性有機物質用触媒構造体。   11. The catalyst structure for a volatile organic material according to claim 10, wherein a ratio of an average particle diameter of the metal fine particles to an average inner diameter of the passage is 1.4 to 3.6. 前記通路の平均内径は、0.1nm〜1.5nmであり、
前記拡径部の内径は、0.5nm〜50nmであることを特徴とする、請求項2〜11のいずれか1項に記載の揮発性有機物質用触媒構造体。
An average inner diameter of the passage is 0.1 nm to 1.5 nm,
12. The catalyst structure for a volatile organic material according to claim 2, wherein an inner diameter of the expanded portion is 0.5 nm to 50 nm.
前記担体の外表面に保持された少なくとも1つの他の揮発性有機物質酸化触媒を更に備えることを特徴とする、請求項1〜12のいずれか1項に記載の揮発性有機物質用触媒構造体。   The catalyst structure for volatile organic substances according to any one of claims 1 to 12, further comprising at least one other volatile organic substance oxidation catalyst held on the outer surface of the carrier. . 前記担体に内在する前記少なくとも1つの揮発性有機物質酸化触媒の含有量が、前記担体の外表面に保持された前記少なくとも1つの他の揮発性有機物質酸化触媒の含有量よりも多いことを特徴とする、請求項13に記載の揮発性有機物質用触媒構造体。   The content of the at least one volatile organic substance oxidation catalyst inherent in the carrier is greater than the content of the at least one other volatile organic substance oxidation catalyst held on the outer surface of the carrier. The catalyst structure for volatile organic substances according to claim 13. 前記ゼオライト型化合物は、ケイ酸塩化合物であることを特徴とする、請求項1〜14のいずれか1項に記載の揮発性有機物質用触媒構造体。   The catalyst structure for volatile organic substances according to any one of claims 1 to 14, wherein the zeolite type compound is a silicate compound. 請求項1〜15のいずれか1項に記載の揮発性有機物質用触媒構造体を有する、揮発性有機物質除去装置。   The volatile organic substance removal apparatus which has the catalyst structure for volatile organic substances of any one of Claims 1-15. ゼオライト型化合物で構成される多孔質構造の担体を得るための前駆体材料(A)に金属含有溶液が含浸された前駆体材料(B)を焼成する焼成工程と、
前記前駆体材料(B)を焼成して得られた前駆体材料(C)を水熱処理する水熱処理工程と、
前記水熱処理された前駆体材料(C)に還元処理を行う工程と、
を有することを特徴とする揮発性有機物質用触媒構造体の製造方法。
A firing step of firing the precursor material (B) obtained by impregnating the precursor material (A) with a metal-containing solution to obtain a porous structure carrier composed of a zeolite-type compound;
A hydrothermal treatment step of hydrothermally treating the precursor material (C) obtained by firing the precursor material (B);
Performing a reduction treatment on the hydrothermally treated precursor material (C);
A process for producing a catalyst structure for volatile organic substances, comprising:
前記焼成工程の前に、非イオン性界面活性剤を、前記前駆体材料(A)に対して50〜500質量%添加することを特徴とする、請求項17に記載の揮発性有機物質用触媒構造体の製造方法。   The catalyst for volatile organic substances according to claim 17, wherein a nonionic surfactant is added in an amount of 50 to 500 mass% with respect to the precursor material (A) before the firing step. Manufacturing method of structure. 前記焼成工程の前に、前記前駆体材料(A)に前記金属含有溶液を複数回に分けて添加することで、前記前駆体材料(A)に前記金属含有溶液を含浸させることを特徴とする、請求項17又は18に記載の揮発性有機物質用触媒構造体の製造方法。   Before the firing step, the precursor material (A) is impregnated with the metal-containing solution by adding the metal-containing solution to the precursor material (A) in a plurality of times. The manufacturing method of the catalyst structure for volatile organic substances of Claim 17 or 18. 前記焼成工程の前に前記前駆体材料(A)に前記金属含有溶液を含浸させる際に、前記前駆体材料(A)に添加する前記金属含有溶液の添加量を、前記前駆体材料(A)に添加する前記金属含有溶液中に含まれる金属元素(M)に対する、前記前駆体材料(A)を構成するケイ素(Si)の比(原子数比Si/M)に換算して、10〜1000となるように調整することを特徴とする、請求項17〜19のいずれか1項に記載の揮発性有機物質用触媒構造体の製造方法。   When the precursor material (A) is impregnated with the metal-containing solution before the firing step, the amount of the metal-containing solution added to the precursor material (A) is changed to the precursor material (A). 10 to 1000 in terms of the ratio of silicon (Si) constituting the precursor material (A) to the metal element (M) contained in the metal-containing solution added to (atom ratio Si / M) It adjusts so that it may become, The manufacturing method of the catalyst structure for volatile organic substances of any one of Claims 17-19 characterized by the above-mentioned. 前記水熱処理工程において、前記前駆体材料(C)と構造規定剤とを混合することを特徴とする、請求項17に記載の揮発性有機物質用触媒構造体の製造方法。   The method for producing a catalyst structure for a volatile organic substance according to claim 17, wherein in the hydrothermal treatment step, the precursor material (C) and a structure directing agent are mixed. 前記水熱処理工程が塩基性雰囲気下で行われることを特徴とする、請求項17に記載の揮発性有機物質用触媒構造体の製造方法。   The method of manufacturing a catalyst structure for a volatile organic material according to claim 17, wherein the hydrothermal treatment step is performed in a basic atmosphere.
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