JP7454142B2 - Photocatalyst manufacturing method and photocatalyst - Google Patents
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Description
本発明は、TiO2系光触媒の製造方法に関し、また光触媒に関する。光触媒とは、光吸収により励起され、酸化反応及び還元反応を引き起こす触媒物質である。「不均一系の半導体光触媒」や「均一系の色素光触媒」があるが、本明細書において、「光触媒」は「不均一系の半導体光触媒」を意味する。半導体光触媒は伝導帯と価電子帯が禁制帯によって隔てられたバンド構造を持つ。バンドギャップ(禁制帯幅)以上のエネルギーを持つ光(電磁波)により、価電子帯の電子が伝導帯へ励起され、価電子帯に正孔が生成する。伝導帯に励起された電子は価電子帯の電子より還元力が強く、暗時では起こらない還元反応を起こすことができる。同様に、正孔も強力な酸化反応を起こす。有機物分解の場合、正孔により有機物が酸化されて、最終的にCO2に完全酸化される。そして、伝導帯に励起された電子は酸素を還元し、最終的に水が生成される。 The present invention relates to a method for producing a TiO2-based photocatalyst, and also relates to a photocatalyst. A photocatalyst is a catalytic substance that is excited by light absorption and causes oxidation and reduction reactions. There are "heterogeneous semiconductor photocatalysts" and "homogeneous dye photocatalysts," and in this specification, "photocatalyst" means "heterogeneous semiconductor photocatalysts." Semiconductor photocatalysts have a band structure in which a conduction band and a valence band are separated by a forbidden band. Light (electromagnetic waves) with energy greater than the band gap (forbidden band width) excites electrons in the valence band to the conduction band, generating holes in the valence band. Electrons excited to the conduction band have a stronger reducing power than electrons in the valence band, and can cause reduction reactions that cannot occur in the dark. Similarly, holes also undergo strong oxidation reactions. In the case of organic matter decomposition, the organic matter is oxidized by holes and finally completely oxidized to CO2. Electrons excited into the conduction band then reduce oxygen, eventually producing water.
TiO2は紫外光領域に吸収を持つ紫外光触媒として知られている。特にアナターゼ型のTiO2は,バンドギャップが3.2eVの金属酸化物半導体であり,紫外光を吸収して高い触媒活性を示すが、可視光領域においては活性を示さない。 TiO2 is known as an ultraviolet photocatalyst that absorbs in the ultraviolet region. In particular, anatase-type TiO2 is a metal oxide semiconductor with a band gap of 3.2 eV and exhibits high catalytic activity by absorbing ultraviolet light, but does not exhibit activity in the visible light region.
これまでの研究では、金属や硫黄や窒素のドーピングによって可視光の吸収及び触媒活性化の試みがなされてきたが、現状は可視光領域において十分かつ実用レベルでの触媒活性を持つ光触媒は報告されていない。 In previous research, attempts have been made to absorb visible light and activate the catalyst by doping with metals, sulfur, and nitrogen, but currently no photocatalysts with sufficient catalytic activity at a practical level in the visible light region have been reported. Not yet.
例えばイオンビームを照射してTiO2のバルク材や薄膜の結晶構造に酸素欠陥を導入し可視光領域で光吸収を持つようにする方法は知られているが、TiO2の粉末等の微細な材料の結晶構造に酸素欠陥を導入し、欠陥量を制御することは容易ではない。 For example, it is known to introduce oxygen defects into the crystal structure of TiO2 bulk materials or thin films by irradiating them with ion beams so that they have light absorption in the visible light region. It is not easy to introduce oxygen defects into the crystal structure and control the amount of defects.
また、CaH2やMgH2を用いてTiO2を還元して、TiO2の亜酸化物を製造することは知られている。得られたTiO2の亜酸化物は、結晶構造が変化しているが、可視光を吸収することが確認されている。しかし、得られたTiO2の亜酸化物は光触媒特性を持たない。この従来技術が障害となって、可視光領域において光触媒活性を有する光触媒を開発する目的で、Mgを用いてTiO2粉末に酸素欠陥を導入することに多くの研究者は挑戦しなかったか、あるいは、挑戦するのが困難であったと考えられる。すなわち、CaH2やMgH2を用いてTiO2を還元して、TiO2の亜酸化物を製造する従来技術は、可視光領域において光触媒活性を有する光触媒を開発する目的で、Mgを用いてTiO2粉末に酸素欠陥を導入しようとする研究開発の動機付けを阻害する要因となっていた。 It is also known to reduce TiO2 using CaH2 or MgH2 to produce a suboxide of TiO2. Although the obtained TiO2 suboxide has a changed crystal structure, it has been confirmed that it absorbs visible light. However, the obtained TiO2 suboxide does not have photocatalytic properties. Due to this conventional technology, many researchers have not attempted to introduce oxygen vacancies into TiO2 powder using Mg in order to develop photocatalysts that have photocatalytic activity in the visible light region, or It may have been difficult to take on the challenge. In other words, the conventional technology of reducing TiO2 using CaH2 or MgH2 to produce suboxides of TiO2 is to reduce oxygen vacancies to TiO2 powder using Mg for the purpose of developing a photocatalyst that has photocatalytic activity in the visible light region. This was a factor that hindered the motivation for research and development to introduce the technology.
再現性があり、また量産性があって、可視光領域において確実な光触媒活性を有する光触媒を製造する方法は知られていなかった。 There has been no known method for producing a photocatalyst that is reproducible, mass-producible, and has reliable photocatalytic activity in the visible light region.
以上のような状況から現在は、紫外光領域ではTiO2系の光触媒が使用され、波長380~800nmの可視光領域ではWO3/CuO系の光触媒が一般的に使用されている。 Under the above circumstances, currently, TiO2-based photocatalysts are generally used in the ultraviolet light region, and WO3/CuO-based photocatalysts are generally used in the visible light region of wavelengths from 380 to 800 nm.
しかしながら、WO3/CuO系の光触媒は可視光領域における揮発性有機化合物(VOC)を完全酸化分解する活性が不十分であるとともにWを原料とするため高価であり資源確保が困難である。本明細書において、「揮発性有機化合物(VOC)」とは、VOC(Volatile Organic Compounds))と呼ばれ、常温常圧で空気中に容易に揮発する有機化合物の総称である。WHOの区分では沸点が50~260℃の有機化合物を示す。ホルムアルデヒドは住宅等の室内空気汚染(シックハウス症候群)の原因物質として知られており、発生源としては、合板、壁紙用接着剤、家具などがある。アセトアルデヒドは実験評価が難しいホルムアルデヒドの代用として光触媒活性を比較する際に使用される最も代表的なVOCであり、またタバコなどの悪臭物質として知られている。トルエンは接着剤や塗料の溶剤及び希釈剤として使用され、内装材等の施工用接着剤・塗料から放散される可能性がある。 However, the WO3/CuO-based photocatalyst has insufficient activity to completely oxidize and decompose volatile organic compounds (VOC) in the visible light region, and since it uses W as a raw material, it is expensive and difficult to secure resources for. In this specification, "Volatile Organic Compounds (VOC)" is a general term for organic compounds that easily volatilize in the air at room temperature and pressure. The WHO classification indicates organic compounds with a boiling point of 50 to 260°C. Formaldehyde is known to be a cause of indoor air pollution in homes (sick building syndrome), and sources include plywood, wallpaper adhesives, and furniture. Acetaldehyde is the most typical VOC used when comparing photocatalytic activity as a substitute for formaldehyde, which is difficult to evaluate experimentally, and is also known as a malodorous substance in tobacco and other substances. Toluene is used as a solvent and diluent for adhesives and paints, and may be emitted from construction adhesives and paints for interior materials, etc.
光触媒として、TiO2粉末とMg、その水素化物又はそれらの混合物の粉末を真空下で350℃以上の高温で反応させると、Mgが徐々に酸化を開始し、TiO2の結晶構造を保持したまま酸素欠陥を導入することができ、可視光吸収を増加させることができるとともに表面積を増加させることができることを本発明者は見出した。 As a photocatalyst, when TiO2 powder is reacted with Mg, its hydride, or a powder of a mixture thereof under vacuum at a high temperature of 350°C or higher, Mg gradually begins to oxidize, and oxygen defects are created while maintaining the crystal structure of TiO2. The present inventors have discovered that visible light absorption can be increased and the surface area can be increased by introducing
エリンガム図は金属の酸化のしやすさを示す広く知られた図表であり、横軸が温度であり、縦軸がギブス自由エネルギーである。ギブス自由エネルギーのマイナス値が大きいほど、酸素との結合力が大きいことを意味している。エリンガム図において、TiとO2からTiO2が生成される際のギブス自由エネルギーと温度との関係は直線で表される。この直線より下方に存在する金属の酸化を表す直線を見つけ出すことによって、TiよりもOとの結合力が大きな金属を理論的に見出すことができる。エリンガム図からMgと同様にTiO2に酸素欠陥を導入できる金属として、Al、Li、Caを理論的に選択することができる。当然、水素にも還元力があり、Al、Li、Mg、Caの水素化物も還元力が強く、TiO2粉末に酸素欠陥を導入することができると理論的に推論することができる。 The Ellingham diagram is a widely known chart showing the ease of oxidation of metals, with the horizontal axis representing temperature and the vertical axis representing Gibbs free energy. The larger the negative value of the Gibbs free energy, the greater the bonding force with oxygen. In the Ellingham diagram, the relationship between Gibbs free energy and temperature when TiO2 is generated from Ti and O2 is represented by a straight line. By finding a straight line that represents the oxidation of metals that exist below this straight line, it is possible to theoretically find a metal that has a stronger bonding force with O than with Ti. From the Ellingham diagram, Al, Li, and Ca can be theoretically selected as metals that can introduce oxygen defects into TiO2 like Mg. Naturally, hydrogen also has a reducing power, and hydrides of Al, Li, Mg, and Ca also have a strong reducing power, and it can be theoretically inferred that oxygen defects can be introduced into the TiO2 powder.
加えて、本発明者は、光触媒の表面に、Fe、Cuなどの金属あるいはその金属酸化物を担持することによって、上記酸素欠陥導入による可視光吸収を妨げることなく、可視光吸収率を更に高めると共に、相乗効果によって光触媒活性を高め、光触媒効率を向上できることを見出した。 In addition, the present inventor has found that by supporting metals such as Fe and Cu or metal oxides thereof on the surface of the photocatalyst, the visible light absorption rate can be further increased without hindering the visible light absorption due to the introduction of oxygen defects. In addition, we discovered that the synergistic effect can enhance photocatalytic activity and improve photocatalytic efficiency.
なお、熱処理温度が550℃を超えると、TiO2の結晶構造がアナターゼ型からルチル型へ変化することを本発明者は見出した。これらの知見によって、本発明のTiO2粉末の結晶構造を保持したまま酸素欠陥を導入すると共に金属を担持する光触媒の製造方法及び光触媒に至ったものである。 The inventors have found that when the heat treatment temperature exceeds 550°C, the crystal structure of TiO2 changes from anatase type to rutile type. Based on these findings, we have arrived at a method for producing a photocatalyst and a photocatalyst in which oxygen defects are introduced while maintaining the crystal structure of TiO2 powder and metal is supported according to the present invention.
第1の本発明に係る光触媒の製造方法は、請求項1に記載のように、TiO2粉末とTiO2に対して0.1~5wt%のAl、Li、Mg若しくはCa、その水素化物又はそれらの混合物の粉末とTiO2に対して0.1~5wt%のFe若しくはCu、その酸化物又はそれらの混合物の粉末とを均一に混合して得た第1の混合粉末をるつぼ内に収納し、前記るつぼを真空加熱炉中に配置し、真空排気した後に、真空中で350~550℃の温度で熱処理して光触媒を製造する。
The method for producing a photocatalyst according to the first aspect of the present invention, as described in
第2の本発明に係る光触媒の製造方法は、請求項2に記載のように、TiO2に対して0.1~5wt%のFe若しくはCu、その酸化物又はそれらの混合物を塩酸又は硝酸で溶解して溶解液を得、前記溶解液とTiO2粉末の水懸濁液とを混合した後に乾燥して得た混合乾燥粉末とTiO2に対して0.1~5wt%のAl、Li、Mg若しくはCa、その水素化物又はそれらの混合物の粉末とを均一に混合して第2の混合粉末を得、前記第2の混合粉末をるつぼ内に収納し、前記るつぼを真空加熱炉中に配置し、真空排気した後に、真空中で350~550℃の温度で熱処理して光触媒を製造する。
The method for producing a photocatalyst according to the second aspect of the present invention, as set forth in
第1又は第2の本発明に係る光触媒の製造方法の好ましい実施態様においては、請求項3に記載のように、TiO2がアナターゼ型、ルチル型、ブルッカイト型又はこれらの混合物である。 In a preferred embodiment of the method for producing a photocatalyst according to the first or second aspect of the present invention, TiO2 is of anatase type, rutile type, brookite type, or a mixture thereof.
第3の本発明は、請求項4に記載のように、TiO2粉末とTiO2に対して0.1~5wt%のAl、Li、Mg若しくはCa、その水素化物又はそれらの混合物の粉末とTiO2に対して0.1~5wt%のFe若しくはCu、その酸化物又はそれらの混合物の粉末とを均一に混合して得た第1の混合粉末をるつぼ内に収納し、前記るつぼを真空加熱炉中に配置し、真空排気した後に、真空中で350~550℃の温度で熱処理して成り、TiO2粉末の結晶構造を保持したまま酸素欠陥を導入すると共にTiO2粉末の表面にFe若しくはCu、その酸化物又はそれらの混合物を担持している。As described in
第4の本発明は、請求項5に記載のように、TiO2に対して0.1~5wt%のFe若しくはCu、その酸化物又はそれらの混合物を塩酸又は硝酸で溶解して溶解液を得、前記溶解液とTiO2粉末の水懸濁液とを混合した後に乾燥して得た混合乾燥粉末とTiO2に対して0.1~5wt%のAl、Li、Mg若しくはCa、その水素化物又はそれらの混合物の粉末とを均一に混合して第2の混合粉末を得、前記第2の混合粉末をるつぼ内に収納し、前記るつぼを真空加熱炉中に配置し、真空排気した後に、真空中で350~550℃の温度で熱処理して成り、TiO2粉末の結晶構造を保持したまま酸素欠陥を導入すると共にTiO2粉末の表面にFe若しくはCu、その酸化物又はそれらの混合物を担持している。The fourth aspect of the present invention is to obtain a solution by dissolving 0.1 to 5 wt% of Fe or Cu, its oxide, or a mixture thereof based on TiO2 with hydrochloric acid or nitric acid. , a mixed dry powder obtained by mixing the solution and an aqueous suspension of TiO2 powder and drying the mixture, and 0.1 to 5 wt% of Al, Li, Mg or Ca, their hydrides, or their hydrides based on TiO2. A second mixed powder is obtained by uniformly mixing the powder of the mixture of The TiO2 powder is heat-treated at a temperature of 350 to 550°C to introduce oxygen defects while maintaining the crystal structure of the TiO2 powder, and to support Fe or Cu, its oxide, or a mixture thereof on the surface of the TiO2 powder.
(1)本発明の光触媒の製造方法においては、固相-固相反応を利用して、還元金属(Al、Li、Mg又はCa)、その水素化物又はそれらの混合物の粉末によってTiO2の粉末の結晶構造を保持したまま酸素欠陥を導入している。得られた粉末をXRD分析したところTiO2の結晶構造が保持されていることが確認された。 (1) In the method for producing a photocatalyst of the present invention, a solid phase-solid phase reaction is used to prepare TiO2 powder using a powder of a reducing metal (Al, Li, Mg, or Ca), its hydride, or a mixture thereof. Oxygen defects are introduced while maintaining the crystal structure. XRD analysis of the obtained powder confirmed that the crystal structure of TiO2 was maintained.
このTiO2粉末の結晶構造を保持したまま酸素欠陥を導入することによって、図13に示すように、TiO2のバンドギャップ(禁制帯幅)の中間に酸素欠陥準位が形成されるため、可視光照射による酸化・還元反応が生じやすくなり、可視光の吸収が増加するとともにTiO2結晶の表面積が増加する。 By introducing oxygen defects while maintaining the crystal structure of this TiO2 powder, an oxygen defect level is formed in the middle of the bandgap (forbidden band width) of TiO2, as shown in Fig. 13, so that it can be irradiated with visible light. oxidation/reduction reactions occur more easily, the absorption of visible light increases and the surface area of the TiO2 crystal increases.
(2)本発明の光触媒の製造方法においては、TiO2の表面へFe又はCu等の金属あるいはその金属酸化物を担持している。このTiO2の表面へのFe又はCu等の金属あるいはその金属酸化物の担持は図14に見られるように酸素欠陥導入による可視光吸収を妨げることなく、可視光吸収率を更に高めると共に、電子伝導性の付与や電荷蓄積効果と相まって可視光におけるTiO2結晶の光触媒活性を高め、光触媒効率を向上させる。 (2) In the method for producing a photocatalyst of the present invention, a metal such as Fe or Cu or a metal oxide thereof is supported on the surface of TiO2. As shown in FIG. 14, supporting metals such as Fe or Cu or their metal oxides on the surface of TiO2 further increases the visible light absorption rate without hindering visible light absorption due to the introduction of oxygen defects, and also increases electron conductivity. Coupled with the imparting properties and the charge accumulation effect, this increases the photocatalytic activity of TiO2 crystals in visible light and improves the photocatalytic efficiency.
以下、本発明の実施例について添付図面を参照して説明する。 Embodiments of the present invention will be described below with reference to the accompanying drawings.
(A)還元金属MgによるTiO2への酸素欠陥を導入した光触媒粉末についての実施例
固相-固相反応によってTiO2粉末とMg粉末から酸素欠陥を導入した光触媒TiO2粉末を製造する実施例について説明する。
(A) Example of a photocatalyst powder in which oxygen defects are introduced into TiO2 by the reduced metal Mg An example of producing a photocatalyst TiO2 powder in which oxygen defects are introduced from TiO2 powder and Mg powder by solid phase-solid phase reaction will be explained. .
<実施例1>
試料粉末の作製
TiO2原料粉末は石原産業(株)製のアナターゼ型であり、純度は85%以上であり、1次粒径は7nmである。
<Example 1>
Preparation of Sample Powder The TiO2 raw material powder is anatase type manufactured by Ishihara Sangyo Co., Ltd., and has a purity of 85% or more and a primary particle size of 7 nm.
Mg原料粉末は、関東金属製であり、純度は99.5%以上であり、平均粒子径D50は100μmである。 The Mg raw material powder is manufactured by Kanto Metals, has a purity of 99.5% or more, and has an average particle diameter D50 of 100 μm.
TiO2原料粉末80.0gとMg原料粉末1.6gを容器内に秤量して、振とうし、その結果として、TiO2原料粉末とMg原料粉末が均一に混合された原料混合粉末を得た。 80.0 g of TiO2 raw powder and 1.6 g of Mg raw powder were weighed into a container and shaken, resulting in a raw mixed powder in which TiO2 raw powder and Mg raw powder were uniformly mixed.
図1は試料粉末作製に使用した製造装置の概略図である。黒鉛るつぼ1は内径φ70mm×高さ125mmであり、上面の中央にガス抜き穴11が設けられている。原料混合粉末2を黒鉛るつぼ1内に収納した後に、高周波加熱装置4を備えた真空加熱炉3内に水平に配置した。
FIG. 1 is a schematic diagram of the manufacturing apparatus used to prepare the sample powder. The
そして、原料混合粉末2が飛散しないように注意しながら、配管5を通じて真空ポンプ6を用いて真空加熱炉3内を8Paまで真空排気した。
Then, the inside of the
8Paまで真空排気した直後に、図2に示す熱処理パターンのように、室温(Tr)~550℃(Tmax)まで1時間(0~t1)かけて昇温し、550℃(Tmax)で3時間(t1~t2)保持し、その後、加熱電源をOFFにして、自然冷却した。昇温、保持、冷却の間も真空ポンプ6を用いて真空排気を続けた。 Immediately after evacuation to 8 Pa, as shown in the heat treatment pattern shown in Figure 2, the temperature was raised from room temperature (Tr) to 550°C (Tmax) over 1 hour (0 to t1), and then at 550°C (Tmax) for 3 hours. The temperature was maintained for (t1 to t2), and then the heating power source was turned off to allow natural cooling. Vacuum evacuation was continued using the vacuum pump 6 during temperature raising, holding, and cooling.
十分に冷却した後、真空ポンプ6を停止し大気圧に戻し、黒鉛るつぼ1を取り出し、試料粉末を得た。
After sufficiently cooling, the vacuum pump 6 was stopped and the pressure returned to atmospheric pressure, and the
得られた試料粉末を目視観察したところ、元の白色粉体が鼠色に色づいた、一様の微粉末であった。 When the obtained sample powder was visually observed, it was found that the original white powder had turned dark brown and was a uniform fine powder.
<実施例1-2>
熱処理パターンを除く他の条件は、まったく実施例1と同様の条件の下で、8Paまで真空排気した直後に、図2に示す熱処理パターンのように、室温(Tr)~350℃(Tmax)まで1時間(0~t1)かけて昇温し、そのまま350℃(Tmax)で3時間(t1~t2)保持し、その後、加熱電源をOFFにして、自然冷却した。昇温、保持、冷却の間も真空ポンプ6を用いて真空排気を続けた。
<Example 1-2>
The other conditions except for the heat treatment pattern were exactly the same as those in Example 1, and immediately after evacuation to 8 Pa, the temperature was raised from room temperature (Tr) to 350°C (Tmax) over 1 hour (0-t1), and the sample was held at 350°C (Tmax) for 3 hours (t1-t2), as shown in the heat treatment pattern in Figure 2, after which the heating power source was turned off and the sample was allowed to cool naturally. Evacuation was continued using the vacuum pump 6 during the heating, holding, and cooling periods.
十分に冷却した後、真空ポンプ6を停止し大気圧に戻し、黒鉛るつぼ1を取り出し、試料粉末を得た。
After sufficiently cooling, the vacuum pump 6 was stopped and the pressure returned to atmospheric pressure, and the
得られた試料粉末を目視観察したところ、元の白色粉体が多少黄色に色づいているが、一様の微粉末であった。 When the obtained sample powder was visually observed, the original white powder was slightly yellowish, but it was found to be a uniform fine powder.
<実施例1-3>
熱処理パターンを除く他の条件は、まったく実施例1と同様の条件の下で、8Paまで真空排気した直後に、図2に示す熱処理パターンのように、室温(Tr)~600℃(Tmax)まで1時間(0~t1)かけて昇温し、そのまま600℃(Tmax)で3時間(t1~t2)保持し、その後、加熱電源をOFFにして、自然冷却した。昇温、保持、冷却の間も真空ポンプ6を用いて真空排気を続けた。
<Example 1-3>
The other conditions except for the heat treatment pattern were exactly the same as those in Example 1, and immediately after evacuation to 8 Pa, the temperature was raised from room temperature (Tr) to 600°C (Tmax) over 1 hour (0-t1), and the sample was held at 600°C (Tmax) for 3 hours (t1-t2), after which the heating power source was turned off and the sample was allowed to cool naturally, as shown in the heat treatment pattern shown in Figure 2. Evacuation was continued using the vacuum pump 6 during the heating, holding, and cooling periods.
十分に冷却した後、真空ポンプ6を停止し大気圧に戻し、黒鉛るつぼ1を取り出し、試料粉末を得た。
After sufficiently cooling, the vacuum pump 6 was stopped and the pressure returned to atmospheric pressure, and the
得られた試料粉末を目視観察したところ、元の白色粉体が黒色に変化した、一様の微粉末であった。 Visual observation of the obtained sample powder revealed that the original white powder had turned black and was a uniform fine powder.
以上の実施例1、実施例1-2、実施例1-3から、TiO2粉末が350℃位の熱処理温度からMgによる酸化還元反応が起こり始めると共に、熱処理温度が高くなるに従ってTiO2の結晶化が進み、550℃位の温度を超えると結晶構造がアナターゼ型からルチル型へと構造変化を起こすことが判明した。 From the above Examples 1, 1-2, and 1-3, the oxidation-reduction reaction by Mg starts to occur in TiO2 powder at a heat treatment temperature of about 350°C, and as the heat treatment temperature increases, TiO2 crystallizes. It was discovered that when the temperature exceeds about 550°C, the crystal structure changes from anatase type to rutile type.
(B)還元金属MgによるTiO2への酸素欠陥を導入するとともに粉末状のFeを用いてFe担持した光触媒粉末についての実施例
固相-固相反応によってTiO2粉末とMg粉末とFe粉末から酸素欠陥を導入するとともにFe担持した光触媒TiO2粉末を製造する実施例について説明する。
(B) Example of photocatalyst powder in which oxygen defects are introduced into TiO2 by reduced metal Mg and Fe is supported using powdered Fe. Oxygen defects are generated from TiO2 powder, Mg powder, and Fe powder by solid phase-solid phase reaction. An example will be described in which a photocatalytic TiO2 powder is introduced and Fe-supported is produced.
<実施例2>
試料粉末の作製
TiO2原料粉末は石原産業(株)製のアナターゼ型であり、純度は85%以上であり、1次粒径は7nmである。
<Example 2>
Preparation of Sample Powder The TiO2 raw material powder is anatase type manufactured by Ishihara Sangyo Co., Ltd., and has a purity of 85% or more and a primary particle size of 7 nm.
Mg原料粉末は、関東金属製であり、純度は99.5%以上であり、平均粒子径D50は100μmである。 The Mg raw material powder is manufactured by Kanto Metals, has a purity of 99.5% or more, and has an average particle diameter D50 of 100 μm.
Fe原料粉末は、Jiangsu Tianyi Ultra Metal Powder Co., Ltd.製であり、純度は98%以上であり、平均粒子径D50は1μmである。 The Fe raw material powder was manufactured by Jiangsu Tianyi Ultra Metal Powder Co. , Ltd. The purity is 98% or more, and the average particle diameter D50 is 1 μm.
TiO2原料粉末80.0gとMg原料粉末0.8gとFe原料粉末0.8gを容器内に秤量して、振とうしたところ、TiO2原料粉末とMg原料粉末とFe原料粉末が均一に混合された原料混合粉末を得た。 When 80.0 g of TiO2 raw powder, 0.8 g of Mg raw powder, and 0.8 g of Fe raw powder were weighed into a container and shaken, the TiO2 raw powder, Mg raw powder, and Fe raw powder were mixed uniformly. A raw material mixed powder was obtained.
図1は試料粉末作製に使用した製造装置の概略図である。黒鉛るつぼ1は内径φ70mm×高さ125mmであり、上面の中央にガス抜き穴11が設けられている。原料混合粉末2を黒鉛るつぼ1内に収納した後に、高周波加熱装置4を備えた真空加熱炉3内に水平に配置した。
FIG. 1 is a schematic diagram of the manufacturing apparatus used to prepare the sample powder. The
そして、原料混合粉末2が飛散しないように注意しながら、配管5を通じて真空ポンプ6を用いて真空加熱炉3内を8Paまで真空排気した。
Then, the inside of the
8Paまで真空排気した直後に、図2に示す熱処理パターンのように、室温(Tr)~500℃(Tmax)まで1時間(0~t1)かけて昇温し、500℃(Tmax)で3時間(t1~t2)保持し、その後、加熱電源をOFFにして、自然冷却した。昇温、保持、冷却の間も真空ポンプ6を用いて真空排気を続けた。 Immediately after evacuation to 8 Pa, as shown in the heat treatment pattern shown in Figure 2, the temperature was raised from room temperature (Tr) to 500°C (Tmax) over 1 hour (0 to t1), and then at 500°C (Tmax) for 3 hours. The temperature was maintained for (t1 to t2), and then the heating power source was turned off to allow natural cooling. Vacuum evacuation was continued using the vacuum pump 6 during temperature raising, holding, and cooling.
十分に冷却した後、真空ポンプ6を停止し大気圧に戻し、黒鉛るつぼ1を取り出し、試料粉末を得た。
After sufficiently cooling, the vacuum pump 6 was stopped to return to atmospheric pressure, and the
得られた試料粉末を目視観察したところ、多少鼠色系に色づいている一様の微粉末であった。 When the obtained sample powder was visually observed, it was found to be a uniform fine powder with a slightly grayish color.
<実施例2-2>
試料粉末の作製
TiO2原料粉末は石原産業(株)製のアナターゼ型であり、純度は85%以上であり、1次粒径は7nmである。
<Example 2-2>
Preparation of Sample Powder The TiO2 raw material powder is anatase type manufactured by Ishihara Sangyo Co., Ltd., and has a purity of 85% or more and a primary particle size of 7 nm.
MgH2原料粉末は、バイオコーク製であり、純度は98%以上であり、平均粒子径D50は60μmである。 The MgH2 raw material powder is manufactured by BioCoke, has a purity of 98% or more, and has an average particle diameter D50 of 60 μm.
Fe原料粉末は、Jiangsu Tianyi Ultra Metal Powder Co., Ltd.製であり、純度は98%以上であり、平均粒子径D50は1μmである。 The Fe raw material powder was manufactured by Jiangsu Tianyi Ultra Metal Powder Co. , Ltd. The purity is 98% or more, and the average particle diameter D50 is 1 μm.
TiO2原料粉末100.0gとMgH2原料粉末1.1gとFe原料粉末1.0gを容器内に秤量して、振とうしたところ、TiO2原料粉末とMgH2原料粉末とFe原料粉末が均一に混合された原料混合粉末を得た。 When 100.0 g of TiO2 raw material powder, 1.1 g of MgH2 raw material powder, and 1.0 g of Fe raw material powder were weighed into a container and shaken, the TiO2 raw material powder, MgH2 raw material powder, and Fe raw material powder were mixed uniformly. A raw material mixed powder was obtained.
図1は試料粉末作製に使用した製造装置の概略図である。黒鉛るつぼ1は内径φ70mm×高さ125mmであり、上面の中央にガス抜き穴11が設けられている。原料混合粉末2を黒鉛るつぼ1内に収納した後に、高周波加熱装置4を備えた真空加熱炉3内に水平に配置した。
FIG. 1 is a schematic diagram of the manufacturing apparatus used to prepare the sample powder. The
そして、原料混合粉末2が飛散しないように注意しながら、配管5を通じて真空ポンプ6を用いて真空加熱炉3内を8Paまで真空排気した。
Then, the inside of the
8Paまで真空排気した直後に、図2に示す熱処理パターンのように、室温(Tr)~500℃(Tmax)まで1時間(0~t1)かけて昇温し、500℃(Tmax)で3時間(t1~t2)保持し、その後、加熱電源をOFFにして、自然冷却した。昇温、保持、冷却の間も真空ポンプ6を用いて真空排気を続けた。昇温時に大きな圧力上昇が認められたが、MgH2が酸化分解してガスが発生したためと考えられる。 Immediately after evacuation to 8 Pa, as shown in the heat treatment pattern shown in Figure 2, the temperature was raised from room temperature (Tr) to 500°C (Tmax) over 1 hour (0 to t1), and then at 500°C (Tmax) for 3 hours. The temperature was maintained for (t1 to t2), and then the heating power source was turned off to allow natural cooling. Vacuum evacuation was continued using the vacuum pump 6 during temperature raising, holding, and cooling. A large pressure increase was observed when the temperature was increased, which is thought to be due to gas generation due to oxidative decomposition of MgH2.
十分に冷却した後、真空ポンプ6を停止し大気圧に戻し、黒鉛るつぼ1を取り出し、試料粉末を得た。After sufficient cooling, the vacuum pump 6 was stopped and the pressure was returned to atmospheric pressure, the
得られた試料粉末を目視観察したところ、多少鼠色がかった白色系に色づいている一様の微粉末であった。 When the obtained sample powder was visually observed, it was found to be a uniform fine powder with a slightly grayish white color.
(C)還元金属MgによるTiO2への酸素欠陥を導入するとともに粉末状のCuを用いてCu担持した光触媒粉末についての実施例
固相-固相反応によってTiO2粉末とMg粉末とCu粉末から酸素欠陥を導入するとともにCu担持した光触媒TiO2粉末を製造する実施例について説明する。
(C) Example of a photocatalyst powder in which oxygen defects are introduced into TiO2 by reduced metal Mg and Cu is supported using powdered Cu. Oxygen defects are generated from TiO2 powder, Mg powder, and Cu powder by solid phase-solid phase reaction. An example of manufacturing a photocatalytic TiO2 powder in which Cu is introduced and Cu is supported will be described.
<実施例3>
試料粉末の作製
TiO2原料粉末は石原産業(株)製のアナターゼ型であり、純度は85%以上であり、1次粒径は7nmである。
<Example 3>
Preparation of Sample Powder The TiO2 raw material powder is anatase type manufactured by Ishihara Sangyo Co., Ltd., and has a purity of 85% or more and a primary particle size of 7 nm.
Mg原料粉末は、関東金属製であり、純度は99.5%以上であり、平均粒子径D50は100μmである。 The Mg raw material powder is manufactured by Kanto Metals, has a purity of 99.5% or more, and has an average particle diameter D50 of 100 μm.
Cu原料粉末は、高純度化学製であり、純度は99.5%以上であり、平均粒子径D50は5μmである。 The Cu raw material powder is manufactured by Kojundo Kagaku Co., Ltd., has a purity of 99.5% or more, and has an average particle diameter D50 of 5 μm.
TiO2原料粉末80.0gとMg原料粉末0.8gとCu原料粉末0.8gを容器内に秤量して、振とうしたところ、TiO2原料粉末とMg原料粉末とCu原料粉末が均一に混合された原料混合粉末を得た。 When 80.0 g of TiO2 raw powder, 0.8 g of Mg raw powder, and 0.8 g of Cu raw powder were weighed into a container and shaken, the TiO2 raw powder, Mg raw powder, and Cu raw powder were mixed uniformly. A raw material mixed powder was obtained.
図1は試料粉末作製に使用した製造装置の概略図である。黒鉛るつぼ1は内径φ70mm×高さ125mmであり、上面の中央にガス抜き穴11が設けられている。原料混合粉末2を黒鉛るつぼ1内に収納した後に、高周波加熱装置4を備えた真空加熱炉3内に水平に配置した。
FIG. 1 is a schematic diagram of the manufacturing apparatus used to prepare the sample powder. The
そして、原料混合粉末2が飛散しないように注意しながら、配管5を通じて真空ポンプ6を用いて真空加熱炉3内を8Paまで真空排気した。
Then, the inside of the
8Paまで真空排気した直後に、図2に示す熱処理パターンのように、室温(Tr)~500℃(Tmax)まで1時間(0~t1)かけて昇温し、500℃(Tmax)で3時間(t1~t2)保持し、その後、加熱電源をOFFにして、自然冷却した。昇温、保持、冷却の間も真空ポンプ6を用いて真空排気を続けた。 Immediately after evacuation to 8 Pa, as shown in the heat treatment pattern shown in Figure 2, the temperature was raised from room temperature (Tr) to 500°C (Tmax) over 1 hour (0 to t1), and then at 500°C (Tmax) for 3 hours. The temperature was maintained for (t1 to t2), and then the heating power source was turned off to allow natural cooling. Vacuum evacuation was continued using the vacuum pump 6 during temperature raising, holding, and cooling.
十分に冷却した後、真空ポンプ6を停止し大気圧に戻し、黒鉛るつぼ1を取り出し、試料粉末を得た。
After sufficiently cooling, the vacuum pump 6 was stopped and the pressure returned to atmospheric pressure, and the
得られた試料粉末を目視観察したところ、全体的に少し鼠色系に色づいている一様の微粉末であった。 When the obtained sample powder was visually observed, it was found to be a uniform fine powder with a slightly gray color overall.
<実施例3-4>
試料粉末に、TiO2原料粉末80.0gとMg原料粉末0.4gとCu原料粉末0.4gを容器内に秤量して、振とうし、TiO2原料粉末とMg原料粉末とCu原料粉末が均一に混合された原料混合粉末を使用した以外は、まったく実施例3と同じ条件で試験を行った。
<Example 3-4>
Weigh 80.0 g of TiO2 raw powder, 0.4 g of Mg raw powder, and 0.4 g of Cu raw powder as sample powders in a container, and shake them to make the TiO2 raw powder, Mg raw powder, and Cu raw powder uniform. The test was conducted under exactly the same conditions as in Example 3 except that the mixed raw material powder was used.
得られた試料粉末を目視観察したところ、全体的に少し茶色系に色づいている一様の微粉末であった。 When the obtained sample powder was visually observed, it was found to be a uniform fine powder with a slightly brownish color overall.
<実施例3-6>
試料粉末に、TiO2原料粉末80.0gとMg原料粉末0.4gとCu原料粉末3.2gを容器内に秤量して、振とうし、TiO2原料粉末とMg原料粉末とCu原料粉末が均一に混合された原料混合粉末を使用した以外は、まったく実施例3と同じ条件で試験を行った。
<Example 3-6>
Weigh out 80.0 g of TiO2 raw powder, 0.4 g of Mg raw powder, and 3.2 g of Cu raw powder as sample powders in a container, and shake them to make the TiO2 raw powder, Mg raw powder, and Cu raw powder uniform. The test was conducted under exactly the same conditions as in Example 3 except that the mixed raw material powder was used.
得られた試料粉末を目視観察したところ、全体的に少し茶色系に色づいている一様の微粉末であった。 When the obtained sample powder was visually observed, it was found to be a uniform fine powder with a slightly brownish color overall.
<実施例3-7>
試料粉末に、TiO2原料粉末80.0gとMg原料粉末3.2gとCu原料粉末0.8gを容器内に秤量し振とうし、TiO2原料粉末とMg原料粉末とCu原料粉末が均一に混合された原料混合粉末を使用した以外は、まったく実施例3と同じ条件で試験を行った。
<Example 3-7>
As sample powders, 80.0 g of TiO2 raw powder, 3.2 g of Mg raw powder, and 0.8 g of Cu raw powder were weighed into a container and shaken, so that the TiO2 raw powder, Mg raw powder, and Cu raw powder were uniformly mixed. The test was conducted under exactly the same conditions as in Example 3, except that the same raw material mixed powder was used.
得られた試料粉末を目視観察したところ、全体的に少し茶色系に色づいている一様の微粉末であった。 When the obtained sample powder was visually observed, it was found to be a uniform fine powder with a slightly brownish color overall.
(D)硝酸鉄溶液によってTiO2粉末に酸化鉄を担持した後に、還元金属MgによるTiO2への酸素欠陥を導入した光触媒粉末についての実施例
硝酸鉄溶液によってTiO2粉末に酸化鉄を担持した後に、固相-固相反応によって酸化鉄を担持したTiO2粉末とMg粉末から酸素欠陥を導入した酸化鉄担持光触媒TiO2粉末を製造する実施例について説明する。
(D) Example of photocatalyst powder in which oxygen defects are introduced into TiO2 by reduced metal Mg after iron oxide is supported on TiO2 powder with iron nitrate solution After iron oxide is supported on TiO2 powder with iron nitrate solution, An example will be described in which an iron oxide-supported photocatalytic TiO2 powder having oxygen vacancies introduced therein is produced from TiO2 powder supporting iron oxide and Mg powder by a phase-solid phase reaction.
<実施例4>
試料粉末の作製
TiO2原料粉末は石原産業(株)製のアナターゼ型であり、純度は85%以上であり、1次粒径は7nmである。
<Example 4>
Preparation of Sample Powder The TiO2 raw material powder is anatase type manufactured by Ishihara Sangyo Co., Ltd., and has a purity of 85% or more and a primary particle size of 7 nm.
Mg原料粉末は、関東金属製であり、純度は99.5%以上であり、平均粒子径D50は100μmである。 The Mg raw material powder is manufactured by Kanto Metals, has a purity of 99.5% or more, and has an average particle diameter D50 of 100 μm.
まず、25~30%硝酸溶液に担持金属であるFeを0.8g溶解した硝酸鉄溶液を作製し、TiO2原料粉末80.0gを水で懸濁させた水懸濁液と前記硝酸鉄溶液とを混合して撹拌する。次にこの混合溶液を170℃以上の温度で乾燥して得た混合乾燥粉末とMg原料粉末0.8gを容器内に秤量して、振とうしたところ、混合乾燥粉末とMg原料粉末が均一に混合された第2原料混合粉末を得た。 First, an iron nitrate solution was prepared by dissolving 0.8 g of Fe as a supported metal in a 25-30% nitric acid solution, and an aqueous suspension in which 80.0 g of TiO2 raw material powder was suspended in water was mixed with the iron nitrate solution. Mix and stir. Next, when the mixed dry powder obtained by drying this mixed solution at a temperature of 170°C or higher and 0.8 g of Mg raw powder were weighed into a container and shaken, the mixed dry powder and Mg raw powder were uniformly mixed. A mixed second raw material mixed powder was obtained.
図1は試料粉末作製に使用した製造装置の概略図である。黒鉛るつぼ1は内径φ70mm×高さ125mmであり、上面の中央にガス抜き穴11が設けられている。第2原料混合粉末2を黒鉛るつぼ1内に収納した後に、高周波加熱装置4を備えた真空加熱炉3内に水平に配置した。
FIG. 1 is a schematic diagram of the manufacturing apparatus used to prepare the sample powder. The
そして、第2原料混合粉末2が飛散しないように注意しながら、配管5を通じて真空ポンプ6を用いて真空加熱炉3内を8Paまで真空排気した。
Then, the inside of the
8Paまで真空排気した直後に、図2に示す熱処理パターンのように、室温(Tr)~500℃(Tmax)まで1時間(0~t1)かけて昇温し、500℃(Tmax)で3時間(t1~t2)保持し、その後、加熱電源をOFFにして、自然冷却した。昇温、保持、冷却の間も真空ポンプ6を用いて真空排気を続けた。 Immediately after evacuation to 8 Pa, as shown in the heat treatment pattern shown in Figure 2, the temperature was raised from room temperature (Tr) to 500°C (Tmax) over 1 hour (0 to t1), and then at 500°C (Tmax) for 3 hours. The temperature was maintained for (t1 to t2), and then the heating power source was turned off to allow natural cooling. Vacuum evacuation was continued using the vacuum pump 6 during temperature raising, holding, and cooling.
十分に冷却した後、真空ポンプ6を停止し大気圧に戻し、黒鉛るつぼ1を取り出し、試料粉末を得た。
After sufficiently cooling, the vacuum pump 6 was stopped and the pressure returned to atmospheric pressure, and the
得られた試料粉末を目視観察したところ、薄黄緑色をした一様の微粉末であった。 When the obtained sample powder was visually observed, it was found to be a uniform fine powder with a pale yellow-green color.
(E)硝酸銅溶液によってTiO2粉末に酸化銅を担持した後に、還元金属MgによってTiO2へ酸素欠陥を導入した光触媒粉末についての実施例
硝酸銅溶液によってTiO2粉末に酸化銅を担持した後に、固相-固相反応によって酸化銅を担持したTiO2粉末とMg粉末から酸素欠陥を導入した酸化銅担持光触媒TiO2粉末を製造する実施例について説明する。
(E) Example of a photocatalyst powder in which copper oxide is supported on TiO2 powder with copper nitrate solution, and then oxygen defects are introduced into TiO2 with reduced metal Mg After supporting copper oxide on TiO2 powder with copper nitrate solution, solid phase - An example will be described in which a copper oxide-supported photocatalyst TiO2 powder having oxygen vacancies introduced therein is produced from TiO2 powder supporting copper oxide and Mg powder by solid-phase reaction.
<実施例5>
試料粉末の作製
TiO2原料粉末は石原産業(株)製のアナターゼ型であり、純度は85%以上であり、1次粒径は7nmである。
<Example 5>
Preparation of Sample Powder The TiO2 raw material powder is anatase type manufactured by Ishihara Sangyo Co., Ltd., and has a purity of 85% or more and a primary particle size of 7 nm.
Mg原料粉末は、関東金属製であり、純度は99.5%以上であり、平均粒子径D50は100μmである。 The Mg raw material powder is manufactured by Kanto Metals, has a purity of 99.5% or more, and has an average particle diameter D50 of 100 μm.
まず、25~30%硝酸溶液に担持金属であるCuを0.8g溶解した硝酸銅溶液を作製し、TiO2原料粉末80.0gを水で懸濁させた水懸濁液と前記硝酸銅溶液とを混合して撹拌する。次にこの混合溶液を170℃以上の温度で乾燥して得た混合乾燥粉末とMg原料粉末0.8gを容器内に秤量して、振とうしたところ、混合乾燥粉末とMg原料粉末が均一に混合された第2原料混合粉末を得た。 First, a copper nitrate solution was prepared by dissolving 0.8 g of Cu, which is a supported metal, in a 25-30% nitric acid solution, and an aqueous suspension in which 80.0 g of TiO2 raw material powder was suspended in water was mixed with the copper nitrate solution. Mix and stir. Next, when the mixed dry powder obtained by drying this mixed solution at a temperature of 170°C or higher and 0.8 g of Mg raw powder were weighed into a container and shaken, the mixed dry powder and Mg raw powder were uniformly mixed. A mixed second raw material mixed powder was obtained.
図1は試料粉末作製に使用した製造装置の概略図である。黒鉛るつぼ1は内径φ70mm×高さ125mmであり、上面の中央にガス抜き穴11が設けられている。第2原料混合粉末2を黒鉛るつぼ1内に収納した後に、高周波加熱装置4を備えた真空加熱炉3内に水平に配置した。
FIG. 1 is a schematic diagram of the manufacturing apparatus used to prepare the sample powder. The
そして、第2原料混合粉末2が飛散しないように注意しながら、配管5を通じて真空ポンプ6を用いて真空加熱炉3内を8Paまで真空排気した。
Then, the inside of the
8Paまで真空排気した直後に、図2に示す熱処理パターンのように、室温(Tr)~500℃(Tmax)まで1時間(0~t1)かけて昇温し、500℃(Tmax)で3時間(t1~t2)保持し、その後、加熱電源をOFFにして、自然冷却した。昇温、保持、冷却の間も真空ポンプ6を用いて真空排気を続けた。 Immediately after evacuation to 8 Pa, as shown in the heat treatment pattern shown in Figure 2, the temperature was raised from room temperature (Tr) to 500°C (Tmax) over 1 hour (0 to t1), and then at 500°C (Tmax) for 3 hours. The temperature was maintained for (t1 to t2), and then the heating power source was turned off to allow natural cooling. Vacuum evacuation was continued using the vacuum pump 6 during temperature raising, holding, and cooling.
十分に冷却した後、真空ポンプ6を停止し大気圧に戻し、黒鉛るつぼ1を取り出し、試料粉末を得た。
After sufficiently cooling, the vacuum pump 6 was stopped and the pressure returned to atmospheric pressure, and the
得られた試料粉末を目視観察したところ、多少茶色系に色づいた一様の微粉末であった。 When the obtained sample powder was visually observed, it was found to be a uniform fine powder with a slightly brownish color.
<実施例5-7>
第2原料混合粉末中におけるCuとMgの割合を変更した以外は、実施例5とまったく同じ条件で試験を行った。
<Example 5-7>
The test was conducted under exactly the same conditions as in Example 5, except that the proportions of Cu and Mg in the second raw material mixed powder were changed.
25~30%硝酸溶液に担持金属であるCuを0.08g溶解した硝酸銅溶液を作製し、TiO2原料粉末80.0gを水で懸濁させた水懸濁液と前記硝酸銅溶液とを混合して撹拌する。次にこの混合溶液を170℃以上の温度で乾燥して得た混合乾燥粉末とMg原料粉末0.4gを容器内に秤量して、振とうしたところ、混合乾燥粉末とMg原料粉末が均一に混合された第2原料混合粉末を得た。 A copper nitrate solution was prepared by dissolving 0.08 g of Cu, which is a supported metal, in a 25-30% nitric acid solution, and a water suspension in which 80.0 g of TiO2 raw material powder was suspended in water was mixed with the copper nitrate solution. and stir. Next, when the mixed dry powder obtained by drying this mixed solution at a temperature of 170°C or higher and 0.4 g of Mg raw powder were weighed into a container and shaken, the mixed dry powder and Mg raw powder were uniformly mixed. A mixed second raw material mixed powder was obtained.
真空中で実施例5と同様の熱処理パターンで加熱、保持、冷却した後、大気圧に戻し、取り出して得られた試料粉末を目視観察したところ、多少茶色系に色づいた一様の微粉末であった。 After heating, holding, and cooling in a vacuum using the same heat treatment pattern as in Example 5, the sample powder was returned to atmospheric pressure and taken out. Visual observation of the obtained sample powder revealed that it was a uniform fine powder with a slight brownish color. there were.
<実施例5-11>
第2原料混合粉末中におけるCuとMgの割合を変更した以外は、実施例5とまったく同じ条件で試験を行った。
<Example 5-11>
The test was conducted under exactly the same conditions as in Example 5, except that the proportions of Cu and Mg in the second raw material mixed powder were changed.
25~30%硝酸溶液に担持金属であるCuを3.2g溶解した硝酸銅溶液を作製し、TiO2原料粉末80.0gを水で懸濁させた水懸濁液と前記硝酸銅溶液とを混合して撹拌する。次にこの混合溶液を170℃以上の温度で乾燥して得た混合乾燥粉末とMg原料粉末0.8gを容器内に秤量して、振とうしたところ、混合乾燥粉末とMg原料粉末が均一に混合された第2原料混合粉末を得た。 A copper nitrate solution was prepared by dissolving 3.2 g of Cu as a supporting metal in a 25 to 30% nitric acid solution, and a water suspension in which 80.0 g of TiO2 raw material powder was suspended in water was mixed with the copper nitrate solution. and stir. Next, when the mixed dry powder obtained by drying this mixed solution at a temperature of 170°C or higher and 0.8 g of Mg raw powder were weighed into a container and shaken, the mixed dry powder and Mg raw powder were uniformly mixed. A mixed second raw material mixed powder was obtained.
真空中で実施例5と同様の熱処理パターンで加熱、保持、冷却した後、大気圧に戻し、取り出して得られた試料粉末を目視観察したところ、多少茶色系に色づいた一様の微粉末であった。 After heating, holding, and cooling in a vacuum using the same heat treatment pattern as in Example 5, the sample powder was returned to atmospheric pressure and taken out. Visual observation of the obtained sample powder revealed that it was a uniform fine powder with a slight brownish color. there were.
<実施例5-12>
第2原料混合粉末中におけるCuとMgの割合を変更した以外は、実施例5とまったく同じ条件で試験を行った。
<Example 5-12>
The test was conducted under exactly the same conditions as in Example 5, except that the proportions of Cu and Mg in the second raw material mixed powder were changed.
25~30%硝酸溶液に担持金属であるCuを0.24g溶解した硝酸銅溶液を作製し、TiO2原料粉末80.0gを水で懸濁させた水懸濁液と前記硝酸銅溶液とを混合して撹拌する。次にこの混合溶液を170℃以上の温度で乾燥して得た混合乾燥粉末とMg原料粉末3.2gを容器内に秤量して、振とうしたところ、混合乾燥粉末とMg原料粉末が均一に混合された第2原料混合粉末を得た。 A copper nitrate solution was prepared by dissolving 0.24 g of Cu, which is a supported metal, in a 25-30% nitric acid solution, and a water suspension in which 80.0 g of TiO2 raw material powder was suspended in water was mixed with the copper nitrate solution. and stir. Next, when the mixed dry powder obtained by drying this mixed solution at a temperature of 170°C or higher and 3.2 g of Mg raw powder were weighed into a container and shaken, the mixed dry powder and Mg raw powder were uniformly mixed. A mixed second raw material mixed powder was obtained.
真空中で実施例5と同様の熱処理パターンで加熱、保持、冷却した後、大気圧に戻し、取り出して得られた試料粉末を目視観察したところ、多少茶色系に色づいた一様の微粉末であった。 After heating, holding, and cooling in a vacuum using the same heat treatment pattern as in Example 5, the sample powder was returned to atmospheric pressure and taken out. Visual observation of the obtained sample powder revealed that it was a uniform fine powder with a slight brownish color. there were.
(F)TiO2の結晶構造の異なる光触媒粉末についての実施例
<実施例6>
試料粉末の作製
TiO2原料粉末は日本アエロジル(株)製のアナターゼ型87%とルチル型13%の混合粉末であり、純度は99%以上であり、1次粒径は20nmである。
(F) Example of photocatalyst powder with different crystal structure of TiO2 <Example 6>
Preparation of Sample Powder The TiO2 raw material powder is a mixed powder of 87% anatase type and 13% rutile type manufactured by Nippon Aerosil Co., Ltd., the purity is 99% or more, and the primary particle size is 20 nm.
Mg原料粉末は、関東金属製であり、純度は99.5%以上であり、平均粒子径D50は100μmである。 The Mg raw material powder is manufactured by Kanto Metals, has a purity of 99.5% or more, and has an average particle diameter D50 of 100 μm.
まず、25~30%硝酸溶液に担持金属であるCuを0.8g溶解した硝酸銅溶液を作製し、TiO2原料粉末80.0gを水で懸濁させた水懸濁液と前記硝酸銅溶液とを混合して撹拌する。次にこの混合溶液を170℃以上の温度で乾燥して得た混合乾燥粉末とMg原料粉末0.8gを容器内に秤量して、振とうしたところ、混合乾燥粉末とMg原料粉末が均一に混合された第2原料混合粉末を得た。 First, a copper nitrate solution was prepared by dissolving 0.8 g of Cu, which is a supported metal, in a 25-30% nitric acid solution, and an aqueous suspension in which 80.0 g of TiO2 raw material powder was suspended in water was mixed with the copper nitrate solution. Mix and stir. Next, when the mixed dry powder obtained by drying this mixed solution at a temperature of 170°C or higher and 0.8 g of Mg raw powder were weighed into a container and shaken, the mixed dry powder and Mg raw powder were uniformly mixed. A mixed second raw material mixed powder was obtained.
図1は試料粉末作製に使用した製造装置の概略図である。黒鉛るつぼ1は内径φ70mm×高さ125mmであり、上面の中央にガス抜き穴11が設けられている。原料粉末2を黒鉛るつぼ1内に収納した後に、高周波加熱装置4を備えた真空加熱炉3内に水平に配置した。
FIG. 1 is a schematic diagram of the manufacturing apparatus used to prepare the sample powder. The
そして、原料粉末2が飛散しないように注意しながら、配管5を通じて真空ポンプ6を用いて真空加熱炉3内を8Paまで真空排気した。
Then, the inside of the
8Paまで真空排気した直後に、図2に示す熱処理パターンのように、室温(Tr)~450℃(Tmax)まで1時間(0~t1)かけて昇温し、450℃(Tmax)で3時間(t1~t2)保持し、その後、加熱電源をOFFにして、自然冷却した。昇温、保持、冷却の間も真空ポンプ6を用いて真空排気を続けた。 Immediately after evacuation to 8 Pa, as shown in the heat treatment pattern shown in Figure 2, the temperature was raised from room temperature (Tr) to 450°C (Tmax) over 1 hour (0 to t1), and then at 450°C (Tmax) for 3 hours. The temperature was maintained for (t1 to t2), and then the heating power source was turned off to allow natural cooling. Vacuum evacuation was continued using the vacuum pump 6 during temperature raising, holding, and cooling.
十分に冷却した後、真空ポンプ6を停止し大気圧に戻し、黒鉛るつぼ1を取り出し、試料粉末を得た。
After sufficiently cooling, the vacuum pump 6 was stopped and the pressure returned to atmospheric pressure, and the
得られた試料粉末を目視観察したところ、薄い黄色の一様の微粉末であった。 When the obtained sample powder was visually observed, it was found to be a pale yellow uniform fine powder.
<実施例6―2>
試料粉末の作製
TiO2原料粉末は高純度化学製のルチル型であり、純度は99%以上であり、1次粒径は500nmである。
<Example 6-2>
Preparation of Sample Powder The TiO2 raw material powder is a rutile type manufactured by Kojundo Chemical Co., Ltd., and has a purity of 99% or more and a primary particle size of 500 nm.
まず、25~30%硝酸溶液に担持金属であるCuを0.8g溶解した硝酸銅溶液を作製し、TiO2原料粉末80.0gを水で懸濁させた水懸濁液と前記硝酸銅溶液とを混合して撹拌する。次にこの混合溶液を170℃以上の温度で乾燥して得た混合乾燥粉末とMg原料粉末0.8gを容器内に秤量して、振とうしたところ、混合乾燥粉末とMg原料粉末が均一に混合された第2原料混合粉末を得た。 First, a copper nitrate solution was prepared by dissolving 0.8 g of Cu, which is a supported metal, in a 25-30% nitric acid solution, and an aqueous suspension in which 80.0 g of TiO2 raw material powder was suspended in water was mixed with the copper nitrate solution. Mix and stir. Next, when the mixed dry powder obtained by drying this mixed solution at a temperature of 170°C or higher and 0.8 g of Mg raw powder were weighed into a container and shaken, the mixed dry powder and Mg raw powder were uniformly mixed. A mixed second raw material mixed powder was obtained.
図1は試料粉末作製に使用した製造装置の概略図である。黒鉛るつぼ1は内径φ70mm×高さ125mmであり、上面の中央にガス抜き穴11が設けられている。原料粉末2を黒鉛るつぼ1内に収納した後に、高周波加熱装置4を備えた真空加熱炉3内に水平に配置した。
FIG. 1 is a schematic diagram of the manufacturing apparatus used to prepare the sample powder. The
そして、原料粉末2が飛散しないように注意しながら、配管5を通じて真空ポンプ6を用いて真空加熱炉3内を8Paまで真空排気した。
Then, the inside of the
8Paまで真空排気した直後に、図2に示す熱処理パターンのように、室温(Tr)~500℃(Tmax)まで1時間(0~t1)かけて昇温し、500℃(Tmax)で3時間(t1~t2)保持し、その後、加熱電源をOFFにして、自然冷却した。昇温、保持、冷却の間も真空ポンプ6を用いて真空排気を続けた。 Immediately after evacuation to 8 Pa, as shown in the heat treatment pattern shown in Figure 2, the temperature was raised from room temperature (Tr) to 500°C (Tmax) over 1 hour (0 to t1), and then at 500°C (Tmax) for 3 hours. The temperature was maintained for (t1 to t2), and then the heating power source was turned off to allow natural cooling. Vacuum evacuation was continued using the vacuum pump 6 during temperature raising, holding, and cooling.
十分に冷却した後、真空ポンプ6を停止し大気圧に戻し、黒鉛るつぼ1を取り出し、試料粉末を得た。
After sufficiently cooling, the vacuum pump 6 was stopped and the pressure returned to atmospheric pressure, and the
得られた試料粉末を目視観察したところ、薄い黄土色をした一様の微粉末であった。 When the obtained sample powder was visually observed, it was found to be a uniform fine powder with a light ocher color.
<実施例6―3>
試料粉末の作製
TiO2原料粉末は高純度化学製のブルッカイト型であり、純度は99%以上であり、1次粒径は30nmである。
<Example 6-3>
Preparation of Sample Powder The TiO2 raw material powder is a brookite type manufactured by Kojundo Kagaku Co., Ltd., and has a purity of 99% or more and a primary particle size of 30 nm.
まず、25~30%硝酸溶液に担持金属であるCuを0.8g溶解した硝酸銅溶液を作製し、TiO2原料粉末80.0gを水で懸濁させた水懸濁液と前記硝酸銅溶液とを混合して撹拌する。次にこの混合溶液を170℃以上の温度で乾燥して得た混合乾燥粉末とMg原料粉末0.8gを容器内に秤量して、振とうしたところ、混合乾燥粉末とMg原料粉末が均一に混合された第2原料混合粉末を得た。 First, a copper nitrate solution was prepared by dissolving 0.8 g of Cu, which is a supported metal, in a 25-30% nitric acid solution, and an aqueous suspension in which 80.0 g of TiO2 raw material powder was suspended in water was mixed with the copper nitrate solution. Mix and stir. Next, when the mixed dry powder obtained by drying this mixed solution at a temperature of 170°C or higher and 0.8 g of Mg raw powder were weighed into a container and shaken, the mixed dry powder and Mg raw powder were uniformly mixed. A mixed second raw material mixed powder was obtained.
図1は試料粉末作製に使用した製造装置の概略図である。黒鉛るつぼ1は内径φ70mm×高さ125mmであり、上面の中央にガス抜き穴11が設けられている。原料粉末2を黒鉛るつぼ1内に収納した後に、高周波加熱装置4を備えた真空加熱炉3内に水平に配置した。
FIG. 1 is a schematic diagram of the manufacturing apparatus used to prepare the sample powder. The
そして、原料粉末2が飛散しないように注意しながら、配管5を通じて真空ポンプ6を用いて真空加熱炉3内を8Paまで真空排気した。
Then, the inside of the
8Paまで真空排気した直後に、図2に示す熱処理パターンのように、室温(Tr)~500℃(Tmax)まで1時間(0~t1)かけて昇温し、500℃(Tmax)で3時間(t1~t2)保持し、その後、加熱電源をOFFにして、自然冷却した。昇温、保持、冷却の間も真空ポンプ6を用いて真空排気を続けた。 Immediately after evacuation to 8 Pa, as shown in the heat treatment pattern shown in Figure 2, the temperature was raised from room temperature (Tr) to 500°C (Tmax) over 1 hour (0 to t1), and then at 500°C (Tmax) for 3 hours. The temperature was maintained for (t1 to t2), and then the heating power source was turned off to allow natural cooling. Vacuum evacuation was continued using the vacuum pump 6 during temperature raising, holding, and cooling.
十分に冷却した後、真空ポンプ6を停止し大気圧に戻し、黒鉛るつぼ1を取り出し、試料粉末を得た。
After sufficiently cooling, the vacuum pump 6 was stopped and the pressure returned to atmospheric pressure, and the
得られた試料粉末を目視観察したところ、ほとんど色づいていない白色の一様の微粉末であった。 When the obtained sample powder was visually observed, it was found to be a uniform white fine powder with almost no coloration.
(G)その他の光触媒粉末についての比較例 (G) Comparative examples of other photocatalyst powders
<比較例>
比較例として市販のアナターゼ型光触媒を入手した。
<Comparative example>
A commercially available anatase type photocatalyst was obtained as a comparative example.
市販のアナターゼ型光触媒は石原産業(株)製のST-01(商品名)であり、純度は87%であり、1次粒径は7nmである。 A commercially available anatase photocatalyst is ST-01 (trade name) manufactured by Ishihara Sangyo Co., Ltd., and has a purity of 87% and a primary particle size of 7 nm.
(H)最終試料粉末の測定
得られた最終試料粉末について、リガク製X線回折装置RINT 2200VK/PCを用いてX線回折分析を行った。測定結果を図3~図5に示す。図3~図5において、曲線は最終試料粉末のX線回折プロファイルであり、アナターゼ型TiO2の標準ピークパターンとともに表示している。図3はアナターゼ型TiO2原料粉末のX線回折プロファイルを示している。図4は実施例1で得られた最終試料粉末のX線回折プロファイルを示している。図4のX線回折プロファイルから分かるように、熱処理温度が550°である実施例1の最終試料粉末は元のアナターゼ型の結晶構造を残したままであることが分かる。
(H) Measurement of Final Sample Powder The obtained final sample powder was subjected to X-ray diffraction analysis using an X-ray diffractometer RINT 2200VK/PC manufactured by Rigaku. The measurement results are shown in Figures 3 to 5. In FIGS. 3 to 5, the curves are the X-ray diffraction profiles of the final sample powders and are displayed along with the standard peak pattern of anatase TiO2. FIG. 3 shows the X-ray diffraction profile of the anatase-type TiO2 raw material powder. FIG. 4 shows the X-ray diffraction profile of the final sample powder obtained in Example 1. As can be seen from the X-ray diffraction profile in FIG. 4, the final sample powder of Example 1, in which the heat treatment temperature was 550°, retains the original anatase crystal structure.
一方、図5は600℃(Tmax)で3時間熱処理にしたときに得られた最終試料粉末のX線回折プロファイルを示している。図5から熱処理温度が600℃になるとアナターゼ型の結晶構造が崩れてルチル型の結晶に変化していくことが分かる。また、熱処理温度が350℃である実施例1-2においては、熱処理温度が300℃近くになると一時的に炉内温度及び気圧が増大する変化が見られることからTiO2とMgの間に酸化還元反応が生じてTiO2の結晶構造に酸素欠陥が導入され始めるが、300℃未満では炉内の温度及び気圧に急激な変化は見られず、還元金属であるMgによるTiO2の還元反応が生じない。このように、最終試料粉末の結晶構造は350℃~550℃の熱処理温度において原料粉末であるTiO2の結晶構造を維持しつつ、結晶化が進むと同時に、還元金属によるTiO2の還元作用と物質拡散等が生じているものと考えられる。 On the other hand, FIG. 5 shows the X-ray diffraction profile of the final sample powder obtained when heat treated at 600° C. (Tmax) for 3 hours. It can be seen from FIG. 5 that when the heat treatment temperature reaches 600° C., the anatase crystal structure collapses and changes to a rutile crystal. In addition, in Example 1-2 where the heat treatment temperature was 350°C, when the heat treatment temperature approached 300°C, there was a change in which the temperature and pressure inside the furnace temporarily increased. A reaction occurs and oxygen defects begin to be introduced into the crystal structure of TiO2, but at temperatures below 300°C, no rapid changes are observed in the temperature and pressure inside the furnace, and the reduction reaction of TiO2 by Mg, which is a reducing metal, does not occur. In this way, the crystal structure of the final sample powder maintains the crystal structure of TiO2, which is the raw material powder, at a heat treatment temperature of 350°C to 550°C, and at the same time as crystallization progresses, the reduction action of TiO2 by the reducing metal and material diffusion occur. It is thought that this is occurring.
光触媒粉末の特性試験
次に、実施例1~6-3の光触媒粉末及び比較例の光触媒粉末についての特性試験について説明する。
Characteristic Test of Photocatalyst Powder Next, a characteristic test of the photocatalyst powder of Examples 1 to 6-3 and the photocatalyst powder of Comparative Example will be explained.
(I)光吸収スペクトルの測定結果
試料粉末を光透過のない厚さで平坦な平板状に成形して分光反射率測定用試料を準備した。
(I) Measurement Results of Light Absorption Spectrum A sample for spectral reflectance measurement was prepared by molding the sample powder into a flat plate with a thickness that did not transmit light.
分光反射率(拡散+正反射率)は、SolidSpec-3700DUV(島津製作所製、ダブルビーム式)を用いて、測定した。 The spectral reflectance (diffuse+specular reflectance) was measured using SolidSpec-3700DUV (manufactured by Shimadzu Corporation, double beam type).
図6は分光反射率(拡散+正反射率)測定の配置を示す概略図である。分光反射率測定用試料の測定部分を包むように積分球を配置する。積分球の鉛直方向から8°傾いた部分に光入口を設けてある。不図示の分光器から特定波長の光が光入口を通って分光反射率測定用試料の測定部分に入射される。そして、反射光を測定して、試料の分光反射率(拡散+正反射率)を測定する。 FIG. 6 is a schematic diagram showing the arrangement for measuring spectral reflectance (diffuse+specular reflectance). An integrating sphere is placed so as to surround the measurement part of the sample for spectral reflectance measurement. The light entrance is provided in a part of the integrating sphere that is inclined by 8 degrees from the vertical direction. Light of a specific wavelength from a spectroscope (not shown) passes through the light inlet and enters the measurement portion of the sample for spectral reflectance measurement. Then, the reflected light is measured to measure the spectral reflectance (diffuse+specular reflectance) of the sample.
250~700nmにおける光吸収スペクトルの測定結果が図7及び図8に比較例と共に示されている。 The measurement results of the optical absorption spectrum in the range from 250 to 700 nm are shown in FIGS. 7 and 8 together with comparative examples.
図7には、実施例1、実施例2、実施例2-2、実施例3、実施例4、実施例5及び比較例で得られた試料粉末の光吸収スペクトルの測定結果が示されている。図8には、実施例5、実施例6、実施例6-2、実施例6-3及び比較例で得られた試料粉末の光吸収スペクトルの測定結果が示されている。350nm以下の波長(紫外光領域)では、実施例1、実施例2、実施例2-2、実施例3、実施例4、実施例5、実施例6、実施例6-2、実施例6-3及び比較例の吸収率は約90~95%であり、ほぼ同等である。400~700nmの波長(可視光領域)においては、実施例1の吸収率が48~18%であり、実施例2の吸収率が62~59%であり、実施例2-2の吸収率が62~58%であり、実施例3の吸収率が30~28%であり、実施例4の吸収率が76~24%であり、実施例5の吸収率が67~42%であり、実施例6の吸収率が62~45%であり、実施例6-2の吸収率が67~35%であり、実施例6-3の吸収率が57~47%であり、比較例の吸収率が28~5%である。実施例1~6-3の光触媒は、いずれも、比較例に比べて、可視光領域での吸収率ははるかに優れていることがわかる。 FIG. 7 shows the measurement results of the light absorption spectra of the sample powders obtained in Example 1, Example 2, Example 2-2, Example 3, Example 4, Example 5, and Comparative Example. There is. FIG. 8 shows the measurement results of the light absorption spectra of the sample powders obtained in Example 5, Example 6, Example 6-2, Example 6-3, and Comparative Example. For wavelengths of 350 nm or less (ultraviolet light region), Example 1, Example 2, Example 2-2, Example 3, Example 4, Example 5, Example 6, Example 6-2, Example 6 The absorption rates of -3 and Comparative Example are about 90 to 95%, which are almost the same. At wavelengths of 400 to 700 nm (visible light region), the absorption rate of Example 1 is 48 to 18%, the absorption rate of Example 2 is 62 to 59%, and the absorption rate of Example 2-2 is The absorption rate of Example 3 is 30-28%, the absorption rate of Example 4 is 76-24%, the absorption rate of Example 5 is 67-42%, and the absorption rate of Example 3 is 30-28%, and the absorption rate of Example 5 is 67-42%. The absorption rate of Example 6 is 62-45%, the absorption rate of Example 6-2 is 67-35%, the absorption rate of Example 6-3 is 57-47%, and the absorption rate of Comparative Example is 62-45%. is 28-5%. It can be seen that all of the photocatalysts of Examples 1 to 6-3 have much better absorption rates in the visible light region than the comparative examples.
実施例2及び実施例2-2の光触媒は比較例の光触媒に比べて、可視光領域における吸収率が特に優れており、紫外光から可視光領域(250~700nm)において、還元材として還元金属(Mg)又はその水素化物(MgH2)を使用してもその光吸収スペクトルは殆ど同じであり、光触媒特性も殆ど同じであることが予測される。また、実施例5、実施例6、実施例6-2、実施例6-3の光触媒は、比較例の光触媒に比べて、可視光領域における吸収率が優れており、アナターゼ型、ルチル型、ブルッカイト型のいずれの結晶型であっても、本発明によって、市販のアナターゼ型光触媒よりも可視光領域における光吸収率を高められることがわかる。 The photocatalysts of Example 2 and Example 2-2 have particularly excellent absorption rates in the visible light region compared to the photocatalysts of comparative examples, and in the ultraviolet to visible light region (250 to 700 nm), reducing metals are used as reducing agents. Even if (Mg) or its hydride (MgH2) is used, its light absorption spectrum is almost the same, and it is predicted that the photocatalytic properties are also almost the same. Furthermore, the photocatalysts of Example 5, Example 6, Example 6-2, and Example 6-3 have better absorption rates in the visible light region than the photocatalysts of the comparative examples, and have anatase type, rutile type, It can be seen that the present invention can increase the light absorption rate in the visible light region more than commercially available anatase type photocatalysts, regardless of the brookite type crystal type.
本実施例の光触媒は、いずれも資源も豊富で安価なTiO2をベースにしており、可視光領域における光触媒として使用されている酸化タングステン光触媒(WO3)のように高価で希少なWを使用せずに、優れた可視光領域の光吸収特性をもたせられることがわかる。 The photocatalysts in this example are all based on TiO2, which is a resource abundant and inexpensive, and do not use expensive and rare W, unlike tungsten oxide photocatalysts (WO3), which are used as photocatalysts in the visible light region. It can be seen that it is possible to provide excellent light absorption properties in the visible light region.
(J)光触媒によるVOC分解評価試験
本発明に係る光触媒は、揮発性有機化合物(VOC)を分解することが期待されている。VOCを分解する能力の優劣を評価するために、気化したイソプロピルアルコール(IPA)が充満した容器内に実施例や比較例の光触媒を配置し、キセノンランプから発する光がUVカットフィルターを通して光触媒に照射されて、時間経過とともに変化するIPA残存率及びCO2発生量を測定した。IPAは光照射された光触媒によって一次分解されアセトンが生成され、アセトンがさらに二次分解されてCO2が発生する反応を利用するものである。
(J) VOC decomposition evaluation test using photocatalyst The photocatalyst according to the present invention is expected to decompose volatile organic compounds (VOC). In order to evaluate the superiority or inferiority of the ability to decompose VOCs, the photocatalysts of Examples and Comparative Examples were placed in a container filled with vaporized isopropyl alcohol (IPA), and light emitted from a xenon lamp was irradiated onto the photocatalysts through a UV cut filter. The residual rate of IPA and the amount of CO2 generated were measured as they changed over time. IPA utilizes a reaction in which acetone is firstly decomposed by a photocatalyst irradiated with light, and acetone is further decomposed secondarily to generate CO2.
図9に光触媒によるVOC分解評価試験に用いた装置の概観を示す。バッチ式パイレックス製反応器を用いて、下記条件で試験を行った。
i) 反応器容量:約392ml
ii) 光源:キセノンランプ300W(波長範囲:300~800nm)
iii) カットフィルター:420nm(420nm以下の波長をカットするときに使用)
iv) 雰囲気:乾燥空気(エアーコンプレッサーより供給)、室温
v) VOC(揮発性有機化合物)種類:IPA(イソプロピルアルコール)
vi) VOC濃度:約258ppm
vii) CO2及びVOCはガスクロマトグラフ(GC)(アジレント(株)製,Agilent 3000A MicroGC)のPlot Qカラム及びOV-1カラムを用いて検出した。CO2濃度はCO2センサー(理研計器(株)製,RI-2150)で測定した空気中の濃度を基にGCの積分値から簡易的に割り出した。VOCの初期濃度は光イオン化ガス検出センサー(RAE Systems社製、MiniRAE 3000)で測定し、系内のVOC濃度減少率はGC積分値の変化から計算した。
Figure 9 shows an overview of the equipment used in the photocatalytic VOC decomposition evaluation test. A test was conducted under the following conditions using a batch type Pyrex reactor.
i) Reactor capacity: approximately 392ml
ii) Light source: xenon lamp 300W (wavelength range: 300-800nm)
iii) Cut filter: 420nm (used to cut wavelengths below 420nm)
iv) Atmosphere: Dry air (supplied from an air compressor), room temperature v) VOC (volatile organic compound) type: IPA (isopropyl alcohol)
vi) VOC concentration: approximately 258 ppm
vii) CO2 and VOC were detected using a Plot Q column and an OV-1 column of a gas chromatograph (GC) (Agilent 3000A MicroGC, manufactured by Agilent, Inc.). The CO2 concentration was simply determined from the GC integral value based on the concentration in the air measured with a CO2 sensor (RI-2150, manufactured by Riken Keiki Co., Ltd.). The initial concentration of VOC was measured with a photoionization gas detection sensor (
図10には、300~800nmの光(紫外光から可視光)を照射した場合における実施例2、実施例2-2、実施例3、実施例3-4、実施例3-6、実施例3-7、実施例4、実施例5及び比較例で得られた試料粉末のVOC分解評価結果が示されている。なお、(a)はVOC残存率(%)を示し、(b)はCO2発生量(ppm)を示す。 FIG. 10 shows Example 2, Example 2-2, Example 3, Example 3-4, Example 3-6, and Example when irradiated with light of 300 to 800 nm (from ultraviolet light to visible light). 3-7, the VOC decomposition evaluation results of sample powders obtained in Example 4, Example 5, and Comparative Example are shown. Note that (a) shows the VOC residual rate (%), and (b) shows the amount of CO2 generated (ppm).
300~800nmの光(紫外光から可視光)を照射した場合には、実施例4を除く実施例3、実施例3-4、実施例3-6、実施例3-7、実施例2、実施例2-2、比較例、実施例5の光触媒は、3時間以内でほとんどのVOCを完全分解しており、実施例3、実施例3-6、実施例2、実施例4、実施例2-2、実施例3-7、比較例、実施例5、実施例4の光触媒の順に、VOCが分解されて発生するCO2の量が多いことがわかる。特に、300~800nmの光(紫外光から可視光)を照射した場合には、実施例3、実施例3-4、実施例3-6、実施例3-7、実施例2、実施例2-2の光触媒は、比較例としたアナターゼ型の光触媒よりCO2の発生量が多く、また実施例5も3時間以降では比較例よりもCO2発生量が多くなると予測され、いずれの光触媒も、比較例の光触媒より光触媒としての性能(光触媒性能)が高いことが分かる。 When irradiated with light of 300 to 800 nm (from ultraviolet light to visible light), Example 3 except Example 4, Example 3-4, Example 3-6, Example 3-7, Example 2, The photocatalysts of Example 2-2, Comparative Example, and Example 5 completely decomposed most of the VOCs within 3 hours, and the photocatalysts of Example 2-2, Comparative Example, and Example 5 completely decomposed most of the VOCs within 3 hours. It can be seen that the amount of CO2 generated by decomposing VOC is larger in the order of photocatalysts 2-2, Example 3-7, Comparative Example, Example 5, and Example 4. In particular, when irradiating with light of 300 to 800 nm (from ultraviolet light to visible light), Example 3, Example 3-4, Example 3-6, Example 3-7, Example 2, Example 2 -2 photocatalyst generates more CO2 than the anatase-type photocatalyst used as a comparative example, and it is predicted that Example 5 will also generate more CO2 than the comparative example after 3 hours. It can be seen that the performance as a photocatalyst (photocatalytic performance) is higher than that of the example photocatalyst.
図11には、420nm以上の光(可視光)を照射した場合における実施例2、実施例3、実施例4、実施例5、実施例5-7、実施例5-11、実施例5-12で得られた試料粉末のVOC分解評価結果が示されている。なお、(a)はVOC残存率(%)を示し、(b)はCO2発生量(ppm)を示す。 FIG. 11 shows Example 2, Example 3, Example 4, Example 5, Example 5-7, Example 5-11, and Example 5- in the case of irradiation with light of 420 nm or more (visible light). The VOC decomposition evaluation results of the sample powder obtained in No. 12 are shown. Note that (a) shows the VOC residual rate (%), and (b) shows the amount of CO2 generated (ppm).
420nm以上の光(可視光)を照射した場合には、比較例の光触媒はほとんど活性を示さない。実施例5の光触媒は14時間の内にVOCの残存率はほぼ0となり、24時間でほぼ完全分解に近い状態にあり、約3000ppmのCO2が発生している。この値は、紫外光から可視光領域における比較例の光触媒のVOC分解によるCO2の発生量とほぼ同等のレベルである。実施例2の光触媒は実施例5には及ばないが、23時間でVOCの残存率はほぼ0となり、24時間で約2500ppmのCO2が発生しており、更にCO2の発生量は多くなると予測され、この値は光触媒として十分な特性を持っていることが分かる。実施例5-7、実施例5-11、実施例5-12はIPAの分解、CO2の発生量共に実施例5には及ばないものの十分な光触媒特性を有している。実施例3や実施例4の光触媒も時間の経過と共にVOCの減少が見られ、またそれに伴ってCO2の発生も見られることから、可視光領域で活性を示す光触媒といえる。実施例2~5のVOCの残存率が、減少後に一旦増加した後に減少する変化は、光照射された光触媒によってIPAが一次分解されアセトンが生成されることによるガス気体の増加のためであり、その後アセトンは二次分解されて容器内のVOCは減少すると同時に完全分解されたCO2量が増加していく。 When irradiated with light of 420 nm or more (visible light), the photocatalyst of the comparative example shows almost no activity. In the photocatalyst of Example 5, the residual rate of VOC became almost 0 within 14 hours, and it was almost completely decomposed in 24 hours, with approximately 3000 ppm of CO2 being generated. This value is approximately at the same level as the amount of CO2 generated by the VOC decomposition of the photocatalyst of the comparative example in the ultraviolet to visible light range. Although the photocatalyst of Example 2 was not as good as Example 5, the residual rate of VOC was almost 0 in 23 hours, and about 2500 ppm of CO2 was generated in 24 hours, and it is predicted that the amount of CO2 generated will further increase. , it can be seen that this value has sufficient characteristics as a photocatalyst. Examples 5-7, 5-11, and 5-12 have sufficient photocatalytic properties, although they are not as good as Example 5 in both IPA decomposition and CO2 generation. The photocatalysts of Examples 3 and 4 also show a decrease in VOC over time, and the generation of CO2 along with this, so they can be said to be photocatalysts that exhibit activity in the visible light region. The change in the residual rate of VOCs in Examples 2 to 5, which increases once after decreasing and then decreases, is due to the increase in gas due to the primary decomposition of IPA by the irradiated photocatalyst and the generation of acetone. Thereafter, the acetone is subjected to secondary decomposition, and the VOC in the container decreases, while at the same time the amount of completely decomposed CO2 increases.
図12には、420nm以上の光(可視光)を照射した場合における、TiO2の結晶型が異なる実施例5、実施例6、実施例6-2、実施例6-3で得られた試料粉末のVOC分解評価結果が示されている。なお、(a)はVOC残存率(%)を示し、(b)はCO2発生量(ppm)を示す。 FIG. 12 shows sample powders obtained in Example 5, Example 6, Example 6-2, and Example 6-3 with different crystal types of TiO2 when irradiated with light of 420 nm or more (visible light). The VOC decomposition evaluation results are shown. Note that (a) shows the VOC residual rate (%), and (b) shows the amount of CO2 generated (ppm).
420nm以上の光(可視光)を照射した場合には、実施例5、6、6-2、6-3の順に、VOCが分解されて発生するCO2の量が減少しており、TiO2の結晶型によって光触媒としての性能が異なることが分かる。実施例5の触媒は可視光領域で非常に高い光触媒性能を示し、比較例の触媒の紫外光から可視光領域で見られるVOC分解によるCO2の発生量と同等の光触媒性能を示している。実施例6、実施例6-2、実施例6-3の可視光領域での光触媒性能は実施例5程ではないが、24時間で数100ppm以上のCO2が発生しており、光触媒性能が高いことが分かる。 When irradiated with light of 420 nm or more (visible light), the amount of CO2 generated by the decomposition of VOCs decreased in the order of Examples 5, 6, 6-2, and 6-3, and the amount of CO2 generated by the decomposition of VOC decreased. It can be seen that the performance as a photocatalyst differs depending on the type. The catalyst of Example 5 exhibits extremely high photocatalytic performance in the visible light region, and exhibits photocatalytic performance equivalent to the amount of CO2 generated by VOC decomposition seen in the ultraviolet to visible light region of the catalyst of the comparative example. The photocatalytic performance in the visible light region of Example 6, Example 6-2, and Example 6-3 is not as good as Example 5, but several hundred ppm or more of CO2 is generated in 24 hours, and the photocatalytic performance is high. I understand that.
本発明に係る光触媒は、紫外光から可視光領域においては、市販の紫外線光触媒に比べてVOC分解能力が優れていると同時に、特に可視光照射した場合においてもVOC分解能力が優れているので、室外で建造物の壁等の汚れ防止に用いることができるばかりでなく、一般家庭や事務所や映画館や自動車や列車(特に地下鉄列車)の室内やトンネル内に設置して、シックハウス原因物質や有害有機化合物を分解して、より健全な環境を保つことができる。また、本発明に係る光触媒を空気中に配置することによって、空気の清浄化に役立つばかりでなく、本発明に係る光触媒を水中に配置すると、大腸菌などを殺菌することができ、水の清浄化にも役立ち、トイレ、風呂、プール、理容院、病院の内部や周辺に配置することによって、衛生的な水の環境を維持することができる。また、本発明に係る光触媒によって、臭いの原因物質を分解することができ、トイレ、風呂、プール、理容院、病院、鉄道列車、自動車の内部や周辺に配置することによって、衛生的で悪臭の少ない環境を維持することができる。 The photocatalyst according to the present invention has superior VOC decomposition ability in the ultraviolet to visible light region compared to commercially available ultraviolet photocatalysts, and also has excellent VOC decomposition ability especially when irradiated with visible light. Not only can it be used outdoors to prevent stains on walls of buildings, etc., but it can also be installed in households, offices, movie theaters, cars, trains (especially subway trains), and inside tunnels to prevent substances that cause sick house syndrome. It can decompose harmful organic compounds and maintain a healthier environment. In addition, by placing the photocatalyst according to the present invention in the air, it not only helps to purify the air, but also when the photocatalyst according to the present invention is placed in water, it can sterilize E. coli etc. and purify water. They can also be placed in or around toilets, baths, swimming pools, barbershops, and hospitals to maintain a sanitary water environment. In addition, the photocatalyst according to the present invention can decompose odor-causing substances, and can be placed inside or around toilets, baths, swimming pools, barbershops, hospitals, railway trains, and automobiles to provide a sanitary and odor-free environment. It is possible to maintain a small environment.
1 黒鉛るつぼ
2 原料混合粉末
3 真空加熱炉
4 高周波加熱装置
5 配管
6 真空ポンプ
11 ガス抜き穴
1
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| JP2003275599A (en) | 2002-03-19 | 2003-09-30 | National Institute Of Advanced Industrial & Technology | Composite photocatalyst for carbon dioxide reduction and carbon dioxide photoreduction method using the same |
| JP2007090336A (en) | 2005-09-01 | 2007-04-12 | Kyushu Institute Of Technology | Photocatalyst, photocatalyst composition, interior building material, paint, synthetic resin molding, fiber, method of using photocatalyst and method of decomposing harmful substances |
| JP2012214348A (en) | 2011-04-01 | 2012-11-08 | National Institute For Materials Science | Method for synthesizing reduction type titanium oxide |
| CN104399464A (en) | 2014-12-09 | 2015-03-11 | 齐鲁工业大学 | Photocatalyst for activation of organic chlorine inert pollutant molecules in water treatment process, as well as preparation method and application of photocatalyst |
| CN105195146A (en) | 2015-09-30 | 2015-12-30 | 中国科学院新疆理化技术研究所 | Preparation method and application of black TiO2 coated metal copper nano photocatalyst |
| JP2018177553A (en) | 2017-04-04 | 2018-11-15 | 東京印刷機材トレーディング株式会社 | Method for producing titanium suboxide particles and titanium suboxide particles |
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| JP2003275599A (en) | 2002-03-19 | 2003-09-30 | National Institute Of Advanced Industrial & Technology | Composite photocatalyst for carbon dioxide reduction and carbon dioxide photoreduction method using the same |
| JP2007090336A (en) | 2005-09-01 | 2007-04-12 | Kyushu Institute Of Technology | Photocatalyst, photocatalyst composition, interior building material, paint, synthetic resin molding, fiber, method of using photocatalyst and method of decomposing harmful substances |
| JP2012214348A (en) | 2011-04-01 | 2012-11-08 | National Institute For Materials Science | Method for synthesizing reduction type titanium oxide |
| CN104399464A (en) | 2014-12-09 | 2015-03-11 | 齐鲁工业大学 | Photocatalyst for activation of organic chlorine inert pollutant molecules in water treatment process, as well as preparation method and application of photocatalyst |
| CN105195146A (en) | 2015-09-30 | 2015-12-30 | 中国科学院新疆理化技术研究所 | Preparation method and application of black TiO2 coated metal copper nano photocatalyst |
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