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JP6540990B2 - Aldehyde removal material using Ru (fcc) support - Google Patents
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JP6540990B2 - Aldehyde removal material using Ru (fcc) support - Google Patents

Aldehyde removal material using Ru (fcc) support Download PDF

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JP6540990B2
JP6540990B2 JP2015039671A JP2015039671A JP6540990B2 JP 6540990 B2 JP6540990 B2 JP 6540990B2 JP 2015039671 A JP2015039671 A JP 2015039671A JP 2015039671 A JP2015039671 A JP 2015039671A JP 6540990 B2 JP6540990 B2 JP 6540990B2
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JP2016159225A (en
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有希 岡田
有希 岡田
小林 真申
真申 小林
横山 正幸
正幸 横山
北川 宏
宏 北川
康平 草田
康平 草田
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Toyobo Co Ltd
Kyoto University NUC
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Kyoto University NUC
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Description

本発明は、Ru(fcc)担持体を用いたアルデヒド類除去材に関するものである。   The present invention relates to an aldehydes removing material using a Ru (fcc) support.

従来より、建物の室内や自動車の車内等でのタバコ臭の主成分であるアセトアルデヒド、あるいは、シックハウス症候群の原因物質として知られているホルムアルデヒド等の除去を目的として、様々な吸着剤の検討がなされている。   Conventionally, various adsorbents have been studied for the purpose of removing acetaldehyde, which is the main component of tobacco odor in the interior of buildings and in cars and the like, or formaldehyde, which is known as a causative agent of sick house syndrome. ing.

その中でも活性炭は、VOC(Volatile Organic Compounds)等を吸着する材料として知られているが、低分子で極性の高い有機物(例えばアセトアルデヒド、ホルムアルデヒド等)を除去することは困難とされている。そこで、上記用途に用いる際は、活性炭にアミン類を担持させて吸着性能を高めることが知られている(特許文献1)。   Among them, activated carbon is known as a material that adsorbs VOC (volatile organic compounds) and the like, but it is considered difficult to remove low molecular weight and highly polar organic matter (for example, acetaldehyde, formaldehyde and the like). Then, when using for the said use, it is known to make an activated carbon carry | support amines and to improve adsorption performance (patent document 1).

しかしながら、上述のアミン類を担持する技術は、担持アミン類の状態が不安定であることから、熱的および経時的な化学変化による失活が起こりやすく、長期的に高い除去性能を保持することは困難であるという問題がある。   However, since the above-described amine-supporting technology is unstable in the state of the supported amines, it is likely to be deactivated by thermal and time-dependent chemical changes, and maintain high removal performance in the long run. There is a problem that is difficult.

一方、VOC除去を目的として、酸化触媒を用いる方法が近年注目されている。前記酸化触媒として、例えば白金を担持した活性炭やアルミナが挙げられる(特許文献2、非特許文献1)。このような白金を担持した酸化触媒は、活性が高く、アルデヒド類の除去にも高い性能を示す。しかし、白金等の貴金属はコストが高く、より安価な触媒または金属の使用が求められているのが現状である。   On the other hand, a method using an oxidation catalyst has attracted attention in recent years for the purpose of removing VOCs. Examples of the oxidation catalyst include activated carbon and alumina supporting platinum (Patent Document 2, Non-Patent Document 1). Such platinum-supported oxidation catalysts are highly active and show high performance for removal of aldehydes. However, precious metals such as platinum are expensive, and the use of less expensive catalysts or metals is now required.

その白金代替として、ルテニウム(Ru)が用いられるようになってきた。Ruは白金等よりも安価であり、酸化触媒としても活性があることわかっているが、通常、六方最密充填構造(hcp)を取るルテニウムの活性を出すには、高温での使用が必要となってくる。   Ruthenium (Ru) has come to be used as a platinum substitute. Ru is less expensive than platinum etc. and is known to be active as an oxidation catalyst, but usually it needs to be used at high temperature to get the activity of ruthenium having a hexagonal close-packed structure (hcp) It will come.

特開昭56−53744号公報Japanese Patent Application Laid-Open No. 56-53744 特開2006−68591号公報JP, 2006-68591, A

Applied Catalysis B: Environmental, 1996, 8, pp. 405-415Applied Catalysis B: Environmental, 1996, 8, pp. 405-415

本発明は、六方最密充填構造(hcp)を取るルテニウム粒子担持体よりも低い温度で、アルデヒド類を効率よく除去できるRu担持体を用いたアルデヒド類除去材の提供を課題として掲げた。   The object of the present invention is to provide an aldehydes removing material using a Ru carrier capable of efficiently removing aldehydes at a temperature lower than a ruthenium particle carrier having a hexagonal close-packed structure (hcp).

本発明者らは上記の課題を解決するために鋭意研究した結果、遂に本発明を完成するに到った。すなわち本発明は、以下の通りである。
1.面心立方格子構造を取るRu(fcc)粒子と担体とから構成されるRu(fcc)担持体を用いたことを特徴とするアルデヒド類除去材。
2.前記担体が、活性炭、活性炭素繊維、アルミナ、シリカ、ゼオライト、複合酸化物および多孔性金属錯体よりなる群から選択される担体である上記1に記載のアルデヒド類除去材。
As a result of intensive studies to solve the above problems, the present inventors have finally completed the present invention. That is, the present invention is as follows.
1. A material for removing aldehydes, characterized in that a Ru (fcc) support composed of Ru (fcc) particles having a face-centered cubic lattice structure and a carrier is used.
2. The aldehydes-removing material according to the above 1, wherein the support is a support selected from the group consisting of activated carbon, activated carbon fibers, alumina, silica, zeolite, composite oxides and porous metal complexes.

本発明によるアルデヒド類除去材は、面心立方格子構造を取るRu(fcc)粒子と担体とから構成されるRu(fcc)担持体を用いるため、通常、六方最密充填構造(hcp)を取るRu(hcp)担持体よりも低い温度で、アルデヒド類を効率よく除去することができる。   The aldehyde removing material according to the present invention usually takes a hexagonal close-packed structure (hcp) because it uses a Ru (fcc) support composed of Ru (fcc) particles having a face-centered cubic lattice structure and a carrier. Aldehydes can be efficiently removed at a temperature lower than that of the Ru (hcp) support.

実施例1のRu(fcc)粒子のTEM画像である。3 is a TEM image of Ru (fcc) particles of Example 1. 実施例1のRu(fcc)粒子の粉末X線回折チャートである。5 is a powder X-ray diffraction chart of Ru (fcc) particles of Example 1. FIG. 比較例1のRu(hcp)粒子のTEM画像である。7 is a TEM image of Ru (hcp) particles of Comparative Example 1; 比較例1のRu(hcp)粒子の粉末X線回折チャートである。5 is a powder X-ray diffraction chart of Ru (hcp) particles of Comparative Example 1;

以下、本発明を詳細に説明する。
本発明のアルデヒド類除去材は、面心立方格子構造を取るRu(fcc)粒子と担体とから構成されるRu(fcc)担持体を用いることを特徴とする。
Hereinafter, the present invention will be described in detail.
The aldehyde removal material of the present invention is characterized by using a Ru (fcc) support composed of Ru (fcc) particles having a face-centered cubic lattice structure and a carrier.

ルテニウム粒子は通常、六方最密充填構造(hcp)を取る。このRu(hcp)粒子では活性を出すための温度が高いが、本発明の面心立方格子構造を取るRu(fcc)粒子は、80℃でも良好なアルデヒド除去率を示す。このRu(fcc)粒子は、原料としてトリス(アセチルアセトナト)ルテニウム(III)を用いることで合成することができる。原料として塩化ルテニウム(III)等のルテニウム塩を用いた場合は、六方最密充填構造を取るRu(hcp)粒子が得られ、面心立方格子構造を取るRu(fcc)粒子は得られない。なお、六方最密充填構造(hcp)か面心立方格子構造(fcc)かは、粉末X線回折で分析することができる。   Ruthenium particles usually take a hexagonal close-packed structure (hcp). Although the temperature for achieving activity is high in this Ru (hcp) particle, the Ru (fcc) particle having a face-centered cubic lattice structure of the present invention exhibits a good aldehyde removal rate even at 80 ° C. The Ru (fcc) particles can be synthesized by using tris (acetylacetonato) ruthenium (III) as a raw material. When a ruthenium salt such as ruthenium (III) chloride is used as a raw material, Ru (hcp) particles having a hexagonal close-packed structure are obtained, and Ru (fcc) particles having a face-centered cubic lattice structure are not obtained. The hexagonal close-packed structure (hcp) or face-centered cubic lattice structure (fcc) can be analyzed by powder X-ray diffraction.

本発明に用いられる担体としては、活性炭、活性炭素繊維(ACF)、アルミナ、シリカ、ゼオライト、複合酸化物、多孔性金属錯体(Porous Coordination Polymers、或いは、Metal Organic Frameworksとも称される)などが挙げられる。複合酸化物としては、セリウムを含む複合酸化物が好ましく、例えば、セリア−ジルコニア複合酸化物などが挙げられる。   Carriers used in the present invention include activated carbon, activated carbon fibers (ACF), alumina, silica, zeolites, composite oxides, porous metal complexes (also referred to as Porous Coordination Polymers or Metal Organic Frameworks), etc. Be The composite oxide is preferably a composite oxide containing cerium, and examples thereof include ceria-zirconia composite oxide and the like.

Ru(fcc)粒子を担体に担持させる方法としては、所望の特性が得られる手法であれば特に制限はされないが、例えばポリビニルピロリドン(PVP)等の保護剤で粒子をコートしながらRu(fcc)ナノ粒子の前駆体であるトリス(アセチルアセトナト)ルテニウム(III)におけるRuイオンを還元性溶媒中で還元処理することにより、Ru(fcc)ナノ粒子を先に合成し、後工程でRu(fcc)粒子を分散させた溶媒中へ担体を加え、溶媒を蒸発乾固させる蒸発乾固法という方法がある。また、Ru(fcc)ナノ粒子の前駆体であるトリス(アセチルアセトナト)ルテニウム(III)におけるRuイオンとそれを担持する担体を、還元性溶媒中に共存させ、Ruイオンを還元処理する方法もある。還元性溶媒としてはトリエチレングリコールが好ましく、150〜250℃で数時間加熱して還元することが好ましい。担体が保護剤と親和性が弱い場合を除いては、すべての担体において前者の蒸発乾固法が使用できる。細孔径の小さな担体(例えば活性炭素繊維、多孔性金属錯体等)に関しては、Ru粒子径よりも細孔径が小さい場合が考えられるので、後者の担体共存下でRuイオンを還元処理する方法が好ましい。得られるRu(fcc)ナノ粒子は、だいたい3〜5nmとなる。   The method for supporting Ru (fcc) particles on a carrier is not particularly limited as long as the desired properties can be obtained. For example, Ru (fcc) is coated with a protective agent such as polyvinyl pyrrolidone (PVP) while the particles are coated. Ru (fcc) nanoparticles are synthesized first by reduction treatment of Ru ions in tris (acetylacetonato) ruthenium (III), which is a precursor of nanoparticles, in a reducing solvent, and Ru (fcc) is post-processed. The carrier is added to a solvent in which particles are dispersed, and the solvent is evaporated to dryness. Also, Ru ions in tris (acetylacetonato) ruthenium (III), which is a precursor of Ru (fcc) nanoparticles, and a carrier supporting the same coexist in a reducing solvent, and the Ru ions are also subjected to reduction treatment. is there. As a reducing solvent, triethylene glycol is preferable, and reduction by heating at 150 to 250 ° C. for several hours is preferable. The former evaporation to dryness method can be used for all carriers except when the carrier has weak affinity with the protective agent. For supports with small pore size (for example, activated carbon fiber, porous metal complex, etc.), it is conceivable that the pore size is smaller than the Ru particle size, so the latter method of reducing Ru ions in the presence of the carrier is preferable . The resulting Ru (fcc) nanoparticles will be approximately 3 to 5 nm.

担体へのRu担持量としては、Ru粒子が担体に対して0.1〜10質量%で担持されるように、Ru粒子の量やRuイオンの濃度を調整することが好ましい。より好ましくは1〜5質量%である。10質量%を超える担持量では、担体に対する金属濃度が高すぎるため、担体に担持はされるが、高分散状態で担持されにくくなるため、好ましくない。   As the amount of Ru supported on the carrier, it is preferable to adjust the amount of Ru particles and the concentration of Ru ions so that the Ru particles are supported at 0.1 to 10% by mass with respect to the carrier. More preferably, it is 1 to 5% by mass. If the amount is more than 10% by mass, the metal concentration with respect to the carrier is too high, so the carrier is supported, but it is difficult to be supported in a highly dispersed state, which is not preferable.

以下、実施例を挙げて本発明をより具体的に説明する。本発明は以下の実施例によって制限を受けるものではなく、前記、後記の趣旨に適合し得る範囲で適当に変更を加えて実施することも勿論可能であり、それらはいずれも本発明の技術的範囲に包含される。なお、実施例および比較例における評価は、以下のようにして行った。   Hereinafter, the present invention will be more specifically described by way of examples. The present invention is not limited by the following examples, and it is of course possible to implement with appropriate modifications as long as it can conform to the above-mentioned and the following effects, and all of them can be technical of the present invention. It is included in the scope. In addition, the evaluation in an Example and a comparative example was performed as follows.

<粉末X線回折測定>
得られた粒子について、粉末X線回折装置(ブルカー・エイエックスエス社製「NEW D8 ADVANCE」を用いて、対称反射法で測定した。測定条件を以下に示す。
1)X線源:CuKα(λ=1.5418Å)40kV 200mA
2)ゴニオメーター:縦型ゴニオメーター
3)検出器:シンチレーションカウンター
4)回折角(2θ)範囲:3〜90°
5)スキャンステップ:0.05°
6)積算時間:0.5秒/ステップ
7)スリット:発散スリット=0.5°、受光スリット=0.15mm、散乱スリット=0.5°
<Powder X-ray diffraction measurement>
The obtained particles were measured by a symmetrical reflection method using a powder X-ray diffractometer ("NEW D8 ADVANCE" manufactured by Bruker AXS Co., Ltd.) The measurement conditions are shown below.
1) X-ray source: CuKα (λ = 1.5418 Å) 40 kV 200 mA
2) Goniometer: Vertical goniometer 3) Detector: Scintillation counter 4) Diffraction angle (2θ) range: 3 to 90 °
5) Scanning step: 0.05 °
6) Integration time: 0.5 sec / step 7) Slit: divergence slit = 0.5 °, light receiving slit = 0.15 mm, scattering slit = 0.5 °

<透過型電子顕微鏡(TEM)観察>
透過型電子顕微鏡(日立製作所製「HT7700」、または日本電子社製「JEM−2200FS」)を用いて、得られたRu粒子を観察した。
<Transmission electron microscope (TEM) observation>
The obtained Ru particles were observed using a transmission electron microscope (“HT7700” manufactured by Hitachi, Ltd. or “JEM-2200FS” manufactured by JEOL Ltd.).

<アルデヒド類ガス流通系吸着試験>
Ru担持体0.229ccをカラムに充填し、試験ガスを0.2L/minで流通させた。試料の入口・出口でのガス濃度を、ホルムアルデメータhtV(株式会社ジェイエムエス)を用いて測定し、その比から除去率を算出した。具体的には、まず、25℃雰囲気下で測定を開始し、1時間後、入口・出口でのガス濃度を測定し、除去率を算出した。次に続けて、80℃雰囲気下に置き、さらに1時間後、入口・出口でのガス濃度を測定し、除去率を算出した。計2時間の測定を行った。評価条件の詳細を以下に示す。
1)測定雰囲気:25℃または80℃雰囲気下
2)圧力:常圧
3)試験ガス組成:ホルムアルデヒド濃度3ppm(25℃、50%RH空気希釈)
4)空間速度:570,000hr-1
5)平均粒子径(測定サンプルの粒子サイズ):355〜500μm
<Aldehyde gas flow system adsorption test>
0.229 cc of Ru carrier was packed into the column, and the test gas was circulated at 0.2 L / min. The gas concentration at the inlet / outlet of the sample was measured using a Form Aldemeter htV (JMS Co., Ltd.), and the removal rate was calculated from the ratio. Specifically, first, measurement was started under an atmosphere of 25 ° C., and after one hour, the gas concentration at the inlet / outlet was measured to calculate the removal rate. Subsequently, the gas was placed under an atmosphere of 80 ° C., and after one hour, the gas concentration at the inlet and outlet was measured to calculate the removal rate. A total of 2 hours of measurement was performed. Details of the evaluation conditions are shown below.
1) Measurement atmosphere: 25 ° C. or 80 ° C. 2) Pressure: normal pressure 3) Test gas composition: Formaldehyde concentration 3 ppm (25 ° C., 50% RH air dilution)
4) Space velocity: 570,000 hr -1
5) Average particle size (particle size of measurement sample): 355 to 500 μm

<実施例1>
トリス(アセチルアセトナト)ルテニウム(III)1.673g(4.2mmol)と保護剤としてのポリビニルピロリドン0.222g(2.0mmol)を還元性溶媒としてのトリエチレングリコール50mlに入れ、撹拌しながら200℃で3時間加熱し、面心立方格子構造を取るRu(fcc)粒子を合成した。そのTEM画像を図1、粉末X線回折チャートを図2に示す。図1のTEM画像から4.1nm〜4.6nm程度の粒子を形成していることが確認できた。また、粉末X線回折のチャートより、面心立方格子構造を取るRu(fcc)粒子が合成されていることが確認できた。
次に上記で合成したRu(fcc)粒子15mgを蒸留水30mlに分散させ、そこに予め、大気中700℃で5時間加熱処理したγ−アルミナ1gを加え、室温で1日撹拌した。その懸濁液を真空下60℃で濃縮乾固させ、1質量%Ru(fcc)担持γ−アルミナを得た。プレスによる加圧とふるいによる分級によって、粒径を355〜500μmに揃えた。その後、アルデヒド類ガス流通系吸着試験を行った。結果を表1に示す。
Example 1
1.63 g (4.2 mmol) of tris (acetylacetonato) ruthenium (III) and 0.222 g (2.0 mmol) of polyvinylpyrrolidone as a protecting agent are placed in 50 ml of triethylene glycol as a reducing solvent, and 200 After heating at 3 ° C. for 3 hours, Ru (fcc) particles having a face-centered cubic lattice structure were synthesized. The TEM image is shown in FIG. 1, and the powder X-ray diffraction chart is shown in FIG. It was confirmed from the TEM image of FIG. 1 that particles of about 4.1 nm to 4.6 nm were formed. Further, it was confirmed from the powder X-ray diffraction chart that Ru (fcc) particles having a face-centered cubic lattice structure were synthesized.
Next, 15 mg of Ru (fcc) particles synthesized above were dispersed in 30 ml of distilled water, and 1 g of γ-alumina which had been heat treated in air at 700 ° C. for 5 hours was added thereto beforehand and stirred at room temperature for 1 day. The suspension was concentrated to dryness under vacuum at 60 ° C. to obtain 1 mass% Ru (fcc) -supported γ-alumina. The particle diameter was adjusted to 355 to 500 μm by pressing with a press and classification with a sieve. Thereafter, an aldehyde-based gas flow system adsorption test was conducted. The results are shown in Table 1.

<比較例1>
塩化ルテニウム1.098g(4.2mmol)と保護剤としてのポリビニルピロリドン0.222g(2.0mmol)を還元性溶媒としてのトリエチレングリコール50mlに入れ、撹拌しながら200℃で3時間加熱し、六方最密充填構造を取るRu(hcp)粒子を合成した。そのTEM画像を図3、粉末X線回折チャートを図4に示す。図3のTEM画像から3.5nm〜4.5nm程度の粒子を形成していることが確認できた。また、粉末X線回折チャートより、六方最密充填構造を取るRu(hcp)粒子が合成されていることが確認できた。
次に上記で合成したRu(hcp)粒子15mgを蒸留水30mlに分散させ、そこに予め、大気中700℃で5時間加熱処理したγ−アルミナ1gを加え、室温で1日撹拌した。その懸濁液を真空下60℃で濃縮乾固させ、1質量%Ru(hcp)担持γ−アルミナを得た。プレスによる加圧とふるいによる分級によって、粒径を355−500μmに揃えた。その後、アルデヒド類ガス流通系吸着試験を行った。結果を表1に示す。
Comparative Example 1
Put 1.098 g (4.2 mmol) of ruthenium chloride and 0.222 g (2.0 mmol) of polyvinylpyrrolidone as a protecting agent into 50 ml of triethylene glycol as a reducing solvent, and heat at 200 ° C. for 3 hours while stirring, Ru (hcp) particles with close packed structure were synthesized. The TEM image is shown in FIG. 3, and the powder X-ray diffraction chart is shown in FIG. It was confirmed from the TEM image of FIG. 3 that particles of about 3.5 nm to 4.5 nm were formed. In addition, it was confirmed from the powder X-ray diffraction chart that Ru (hcp) particles having a hexagonal close-packed structure were synthesized.
Next, 15 mg of Ru (hcp) particles synthesized above were dispersed in 30 ml of distilled water, and 1 g of γ-alumina which had been heat-treated in air at 700 ° C. for 5 hours was added thereto beforehand and stirred at room temperature for 1 day. The suspension was concentrated to dryness under vacuum at 60 ° C. to obtain 1 mass% Ru (hcp) -supported γ-alumina. The particle size was adjusted to 355-500 μm by pressing with a press and classification with a sieve. Thereafter, an aldehyde-based gas flow system adsorption test was conducted. The results are shown in Table 1.

表1から明らかなように、Ru(fcc)粒子を担持させた担持体を用いた実施例1では、80℃でのホルムアルデヒド除去率が44%と高い。比較例1ではより高温にしなければ40%以上の除去率が達成できないことから、本発明の有用性は明らかである。   As is clear from Table 1, in Example 1 using a support on which Ru (fcc) particles are supported, the formaldehyde removal rate at 80 ° C. is as high as 44%. The utility of the present invention is evident from Comparative Example 1 because a removal rate of 40% or more can not be achieved unless the temperature is raised.

本発明のアルデヒド類除去材は、室内や車内のアルデヒド類を除去する効果に優れているので、より快適な空間を提供し、シックハウス症候群等の疾病を減少させることができる。また面心立方格子構造を取るRu(fcc)担持体を用いているため、Pt系触媒より安価であり、産業界に大きく寄与することができると考える。   Since the aldehydes removal material of the present invention is excellent in the effect of removing aldehydes indoors and in the car, it can provide a more comfortable space and reduce diseases such as sick house syndrome. In addition, since a Ru (fcc) support having a face-centered cubic lattice structure is used, it is cheaper than a Pt-based catalyst, and it can be greatly contributed to the industrial world.

Claims (2)

面心立方格子構造のRu(fcc)粒子と担体とから構成されるRu(fcc)担持体を用いたことを特徴とするアルデヒド類除去材。   A material for removing aldehydes characterized by using a Ru (fcc) support composed of Ru (fcc) particles of a face-centered cubic lattice structure and a carrier. 前記担体が、活性炭、活性炭素繊維、アルミナ、シリカ、ゼオライト、複合酸化物および多孔性金属錯体よりなる群から選択される担体である請求項1に記載のアルデヒド類除去材。   The material for removing aldehydes according to claim 1, wherein the support is a support selected from the group consisting of activated carbon, activated carbon fibers, alumina, silica, zeolite, composite oxides and porous metal complexes.
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