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JP4422147B2 - Photocatalytic activity evaluation method and photocatalytic activity evaluation apparatus - Google Patents
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JP4422147B2 - Photocatalytic activity evaluation method and photocatalytic activity evaluation apparatus - Google Patents

Photocatalytic activity evaluation method and photocatalytic activity evaluation apparatus Download PDF

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JP4422147B2
JP4422147B2 JP2006520507A JP2006520507A JP4422147B2 JP 4422147 B2 JP4422147 B2 JP 4422147B2 JP 2006520507 A JP2006520507 A JP 2006520507A JP 2006520507 A JP2006520507 A JP 2006520507A JP 4422147 B2 JP4422147 B2 JP 4422147B2
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晴夫 井上
行正 呉
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Description

本発明は、金属酸化物半導体の光触媒活性評価方法及び装置に係り、特に寿命の短い活性酸素の測定に適した光触媒活性評価方法及び装置に関する。   The present invention relates to a photocatalytic activity evaluation method and apparatus for metal oxide semiconductors, and more particularly to a photocatalytic activity evaluation method and apparatus suitable for measuring active oxygen having a short lifetime.

二酸化チタン(TiO2)などの光触媒は光照射下で、OHラジカル、スーパーオキサイドイオン、過酸化水素などの活性酸素を発生させ、これらの活性酸素がさらに有機化合物と反応し、有機化合物を完全分解することが周知である。しかし、TiO2などの光触媒は、その合成方法、触媒調整方法などによってその活性が大きく異なることが知られており、その活性を評価する方法の開発が課題とされている。   Photocatalysts such as titanium dioxide (TiO2) generate active oxygen such as OH radicals, superoxide ions, and hydrogen peroxide under light irradiation, and these active oxygens further react with organic compounds to completely decompose the organic compounds. It is well known. However, it is known that the activity of photocatalysts such as TiO2 varies greatly depending on the synthesis method, catalyst preparation method, and the like, and development of a method for evaluating the activity has been an issue.

従来、励起されたキャリア、正孔数測定法として、パルス光で光触媒を照射し、半導体光触媒表面にパルスレーザー光を照射し、表面に励起されたキャリアあるいは正孔数数をカウントすることで、その物質の光触媒性能を短時間で評価する技術が開示されている(例えば、特許文献1参照)。   Conventionally, as a method for measuring excited carriers and holes, the photocatalyst is irradiated with pulsed light, the surface of the semiconductor photocatalyst is irradiated with pulsed laser light, and the number of carriers or holes excited on the surface is counted. A technique for evaluating the photocatalytic performance of the substance in a short time is disclosed (for example, see Patent Document 1).

また、時間分解赤外分光法による光触媒の評価法としては、時間分解赤外分光法を用いて、光触媒の光励起キャリアの動的挙動を観測し、該観測結果に基づいて光触媒の性能を評価することを特徴とする、時間分解赤外分光法による光触媒を評価する方法が開示されている(例えば、特許文献2参照)。   In addition, as a photocatalyst evaluation method using time-resolved infrared spectroscopy, time-resolved infrared spectroscopy is used to observe the dynamic behavior of photoexcited carriers of the photocatalyst and evaluate the performance of the photocatalyst based on the observation results. A method for evaluating a photocatalyst by time-resolved infrared spectroscopy is disclosed (for example, see Patent Document 2).

また、表面電位測定に基づく方法として、光触媒を親水化した後、電解液中に浸漬させて光触媒層表面に電解液を接触させ、ポテンショスタットで自然電位を測定することにより、活性光の照射時間に伴う表面電位を測定する技術が開示されている(例えば、特許文献3参照)。   In addition, as a method based on the surface potential measurement, the photocatalyst is hydrophilized and then immersed in the electrolyte solution, the electrolyte solution is brought into contact with the surface of the photocatalyst layer, and the natural potential is measured with a potentiostat. Has disclosed a technique for measuring the surface potential associated with (see, for example, Patent Document 3).

さらに、メチレンブルーなどの色素の吸光度あるいは反射率の測定に基づく方法として、光触媒反応により色素が分解され、吸光度あるいは反射率の変化を測定することにより光触媒性能を評価する技術が開示されている(例えば、特許文献4参照)。
特開2002−257812号公報 特開2004−205256号公報 特開2004−138387号公報 特開2004−85375号公報
Furthermore, as a method based on the measurement of the absorbance or reflectance of a dye such as methylene blue, a technique is disclosed in which the dye is decomposed by a photocatalytic reaction and the photocatalytic performance is evaluated by measuring a change in absorbance or reflectance (for example, , See Patent Document 4).
JP 2002-257812 A JP 2004-205256 A JP 2004-138387 A JP 2004-85375 A

しかしながら、化学発光法によるものにあっては、化学発光信号は秒単位で測定されているので、寿命が長い活性酸素しか測定できない。特に、TiO2などが示す光触媒活性で最も重要な役割を担うとされている寿命の短いOHラジカルの測定は、これらの方法では測定できないという問題がある。   However, in the case of the chemiluminescence method, since the chemiluminescence signal is measured in seconds, only active oxygen having a long lifetime can be measured. In particular, there is a problem that the measurement of OH radicals having a short lifetime, which is said to play the most important role in the photocatalytic activity exhibited by TiO 2 or the like, cannot be measured by these methods.

また、光触媒反応による有機物の最終的な分解は、薄い濃度の試料でも光触媒反応による分解には数十分から数十時間を要する。このことは、光触媒の有機物分解力の評価には数十分から数十時間掛かることを示している。   Further, the final decomposition of the organic substance by the photocatalytic reaction requires several tens of minutes to several tens of hours for the decomposition by the photocatalytic reaction even with a thin sample. This indicates that it takes several tens of minutes to several tens of hours to evaluate the organic substance decomposing ability of the photocatalyst.

本発明は、このような問題を解決するために、TiO2などの金属酸化物半導体の光触媒活性及び有機物に対する分解特性を、迅速かつ、正確に評価する方法及ぴ装置を提案するものである。   In order to solve such a problem, the present invention proposes a method and apparatus for quickly and accurately evaluating the photocatalytic activity of a metal oxide semiconductor such as TiO 2 and the decomposition characteristics with respect to organic substances.

発明者らは鋭意研究の結果、金属酸化物半導体にルミノールを添加した溶液にパルスレーザーを照射し、生成する活性酸素、特に短寿命活性酸素(OHラジカル、スーパーオキシドイオン)とルミノールとの化学発光反応に伴う化学発光信号強度を測定することにより、金属酸化物半導体の光触媒特性を評価できることを見出し、試験により確認して以下の発明を完成した。すなわち、
(1)本発明に係る金属酸化物半導体の光触媒活性評価方法は、評価対象の金属酸化物半導体とルミノールを含む溶液にパルスレーザーを照射し、発生する活性酸素とルミノールとの反応に伴う化学発光信号強度に基づいて、活性酸素発生量を求めることにより光触媒活性を評価することを特徴とする。
As a result of diligent research, the inventors radiated a pulse laser to a solution in which luminol is added to a metal oxide semiconductor, and chemiluminescence of generated active oxygen, particularly short-lived active oxygen (OH radical, superoxide ion) and luminol. By measuring the intensity of the chemiluminescence signal accompanying the reaction, it was found that the photocatalytic properties of the metal oxide semiconductor could be evaluated. That is,
(1) The method for evaluating the photocatalytic activity of a metal oxide semiconductor according to the present invention comprises irradiating a pulse laser to a solution containing a metal oxide semiconductor to be evaluated and luminol, and chemiluminescence accompanying the reaction between the generated active oxygen and luminol. It is characterized in that the photocatalytic activity is evaluated by determining the amount of active oxygen generation based on the signal intensity.

本発明において、「金属酸化物半導体」としては二酸化チタン(TiO2)又は酸化亜鉛(ZnO)を用いることができる。さらに、GaP、ZrO2、Si、CdS、KTaO3、CdSe、SrTiO3、Nb2O5等、種々の金属酸化物を対象とすることができる。   In the present invention, titanium dioxide (TiO 2) or zinc oxide (ZnO) can be used as the “metal oxide semiconductor”. Furthermore, various metal oxides such as GaP, ZrO2, Si, CdS, KTaO3, CdSe, SrTiO3, and Nb2O5 can be targeted.

本発明において、「活性酸素発生量」は濃度等を含む概念であり、化学発光信号強度データの積分値がレーザー照射により発生する活性酸素量に比例することを用いるものである。   In the present invention, “active oxygen generation amount” is a concept including concentration and the like, and uses that the integrated value of chemiluminescence signal intensity data is proportional to the amount of active oxygen generated by laser irradiation.

本発明に用いるパルスレーザーとしては、波長400nm以下のパルスレーザーであることが望ましく、かつ、レーザー照射後、10ms以内の化学発光信号強度データを用いることが必要である。特に、10ms以内に消滅する短寿命活性酸素であるOHラジカルの発生量を正確に把握するためには、上記条件による評価が必要である。   The pulse laser used in the present invention is preferably a pulse laser having a wavelength of 400 nm or less, and it is necessary to use chemiluminescence signal intensity data within 10 ms after laser irradiation. In particular, in order to accurately grasp the generation amount of OH radicals, which are short-lived active oxygens that disappear within 10 ms, evaluation based on the above conditions is necessary.

本発明において、化学発光信号強度データの最大値又は発光信号強度の積分値に基づいて光触媒活性度を評価することができる。活性酸素発生量は、ほぼ化学発光信号強度の最大値又は発光信号強度の積分値に比例すると見做せるため、この値を用いることが簡易である。
(2)本発明に係る金属酸化物半導体の光触媒活性評価装置は、評価対象の金属酸化物半導体とルミノールを含む溶液を収めた光学セルと、該光学セルにパルスレーザーを照射する手段と、前記パルスレーザーの光軸とほぼ直角方向に置かれ、パルスレーザー照射による前記溶液からの発光を検出して化学発光信号強度を取得する化学発光信号強度取得手段と、化学発光信号強度データに基づいて活性酸素発生量を演算する手段と、を備えて成ることを特徴とする。
In the present invention, the photocatalytic activity can be evaluated based on the maximum value of the chemiluminescence signal intensity data or the integral value of the luminescence signal intensity. Since it can be considered that the amount of generated active oxygen is substantially proportional to the maximum value of the chemiluminescence signal intensity or the integral value of the luminescence signal intensity, it is easy to use this value.
(2) An apparatus for evaluating a photocatalytic activity of a metal oxide semiconductor according to the present invention includes an optical cell containing a solution containing a metal oxide semiconductor to be evaluated and luminol, means for irradiating the optical cell with a pulse laser, A chemiluminescence signal intensity acquisition means which is placed substantially perpendicular to the optical axis of the pulse laser and detects chemiluminescence signal intensity by detecting light emission from the solution by pulse laser irradiation, and active based on the chemiluminescence signal intensity data And means for calculating the amount of oxygen generation.

この場合、光学セルと発光検出手段の経路中にレーザー散乱光除去手段を配置することができる。本手段を配置することにより、レーザー光による誤差を除去することができる。また、「レーザー散乱光除去手段」として、ノッチフィルタを用いることができる。   In this case, the laser scattered light removing means can be arranged in the path between the optical cell and the light emission detecting means. By arranging this means, errors due to laser light can be removed. Further, a notch filter can be used as the “laser scattered light removing means”.

また、光学セルと発光検出手段の経路中に、分光器又はフィルタを配置することができる。分光器の配置により、不純物による誤差の影響を排除することが可能となる。
(3)また、本発明に係る金属酸化物半導体の有機物に対する分解活性評価方法は、有機物とルミノールとを含む溶液にパルスレーザーを照射し、有機物の光触媒反応により発生した活性酸素との分解反応に伴うルミノールの時間分解化学発光信号強度を求め、このデータと上述の各方法による発生活性酸素種とルミノールとの反応に伴う時間分解化学発光信号強度とを比較することを特徴とする。
Further, a spectroscope or a filter can be disposed in the path between the optical cell and the light emission detection means. The arrangement of the spectroscope makes it possible to eliminate the influence of errors due to impurities.
(3) In addition, the method for evaluating the decomposition activity of a metal oxide semiconductor according to the present invention is applied to a decomposition reaction with active oxygen generated by a photocatalytic reaction of an organic material by irradiating a solution containing the organic material and luminol with a pulsed laser. The time-resolved chemiluminescence signal intensity of the accompanying luminol is obtained, and this data is compared with the time-resolved chemiluminescence signal intensity associated with the reaction of the generated active oxygen species and luminol by the above-described methods.

図5は、本発明の作用を概念的に示した図である。同図において、(A)はTiO2などの金属酸化物半導体の懸濁液にルミノールを添加した後に、レーザーを照射したときの時間分解化学発光信号強度を示すものであり、一方、(B)は上記溶液にさらに有機物を含む溶液の場合の時間分解化学発光信号強度を示すものである。両者の信号強度最大値同士の差D、又は積分値の差を求めることにより、金属酸化物半導体の有機物に対する分解活性を評価することができる。   FIG. 5 is a diagram conceptually showing the operation of the present invention. In the figure, (A) shows the time-resolved chemiluminescence signal intensity when a laser is irradiated after adding luminol to a suspension of a metal oxide semiconductor such as TiO2, while (B) is The time-resolved chemiluminescence signal intensity | strength in the case of the solution which further contains an organic substance in the said solution is shown. By obtaining the difference D between the signal intensity maximum values or the difference between the integral values, the decomposition activity of the metal oxide semiconductor with respect to the organic matter can be evaluated.

本発明によれば、金属酸化物半導体の光触媒活性及び有機物に対する分解特性を、迅速かつ、正確に評価することが可能となる。   ADVANTAGE OF THE INVENTION According to this invention, it becomes possible to evaluate rapidly and correctly the photocatalytic activity of a metal oxide semiconductor, and the decomposition characteristic with respect to an organic substance.

以下、本発明に係る光触媒活性評価方法及び光触媒活性評価装置の実施形態について、さらに詳細に説明する。なお、本発明の範囲は特許請求の範囲記載のものであって、以下の実施形態に限定されないことはいうまでもない。   Hereinafter, embodiments of the photocatalytic activity evaluation method and the photocatalytic activity evaluation apparatus according to the present invention will be described in more detail. Needless to say, the scope of the present invention is described in the claims and is not limited to the following embodiments.

図1は、本発明の一実施形態に係る光触媒活性評価装置1の全体構成を示す図である。光触媒活性評価装置1は、レーザー照射装置2、レーザー照射装置2からのパルス光の特定波長を分離するための分散プリズム3、分散プリズム3を出た分離レーザー光の光軸上に集光レンズ4aを介して配置される光学セル5、レーザー光軸と直角方向の光軸上に配置されるレンズ系4b・4c、分光器7及び光電子増倍管(PMT)8を備えている。さらに、PMT8の出力側には検出信号の時間推移を測定するデジタルオシロスコープ9が接続されている。また、レンズ系4b・4cの間には、レーザー散乱光を除去するためのノッチフィルタ6を1枚介在させてある。光学セル5内には、TiO2粉末にルミノールを添加した水溶液が封入されている。本発明に用いるノッチフィルタとしては、例えばNd:Yagレーザーの第三高調波を使う場合、(株)エス・ティ・ジャパンのHNF355ノッチフィルタを用いることができる。   FIG. 1 is a diagram showing an overall configuration of a photocatalytic activity evaluation apparatus 1 according to an embodiment of the present invention. The photocatalytic activity evaluation device 1 includes a laser irradiation device 2, a dispersion prism 3 for separating a specific wavelength of pulsed light from the laser irradiation device 2, and a condensing lens 4a on the optical axis of the separated laser light emitted from the dispersion prism 3. , A lens system 4b and 4c arranged on an optical axis perpendicular to the laser optical axis, a spectrometer 7 and a photomultiplier tube (PMT) 8. Further, a digital oscilloscope 9 for measuring the time transition of the detection signal is connected to the output side of the PMT 8. In addition, one notch filter 6 for removing laser scattered light is interposed between the lens systems 4b and 4c. In the optical cell 5, an aqueous solution obtained by adding luminol to TiO 2 powder is enclosed. As the notch filter used in the present invention, for example, when using the third harmonic of an Nd: Yag laser, an HNF355 notch filter manufactured by ST Japan Co., Ltd. can be used.

次に、光触媒活性評価装置1によるTiO2試料の触媒活性測定は以下のように行われる。レーザー照射装置2から照射されるパルスレーザー光は分散プリズム3によって光触媒を励起できる波長の光(例えばNd:Yagレーザーの場合、第三高調波)が分離され、この光がレンズを介して光学セル5に入射する。これにより励起された光学セル5内のTiO2表面で発生する活性酸素とルミノールとの反応により化学発光が生ずる。化学発光信号は、レンズ系4b・4cにより集光されて分光器7に導入され、さらに分光された光はPMT8により検出・増幅されて、その信号はデジタルオシロスコープに取り込まれる。このようにして求めた時間分解化学発光信号強度(最大発光強度あるいは、全発光時間内の発光強度の積分値)は、TiO2光触媒反応過程で発生する活性酸素の濃度あるいは量に比例する。すなわち、時間分解化学発光信号からTiO2光触媒反応に由来する活性酸素の定量を行うことができる。なお、本発明に用いる分光器としては、例えば(株)日本ローバーのSP-308、PMTとしては、例えば浜松ホットニックスの928を挙げることができる。また、分光器に替えてルミノールの化学発光を通すフィルタを用いることもできる。   Next, the catalytic activity measurement of the TiO2 sample by the photocatalytic activity evaluation apparatus 1 is performed as follows. The pulsed laser light emitted from the laser irradiation device 2 is separated into light having a wavelength that can excite the photocatalyst by the dispersion prism 3 (for example, the third harmonic in the case of an Nd: Yag laser), and this light is transmitted through the lens to the optical cell. 5 is incident. Thus, chemiluminescence is generated by the reaction between the active oxygen generated on the surface of TiO 2 in the optical cell 5 thus excited and luminol. The chemiluminescence signal is collected by the lens systems 4b and 4c and introduced into the spectroscope 7. Further, the separated light is detected and amplified by the PMT 8, and the signal is captured by a digital oscilloscope. The time-resolved chemiluminescence signal intensity (the maximum emission intensity or the integrated value of the emission intensity within the entire emission time) thus determined is proportional to the concentration or amount of active oxygen generated in the TiO 2 photocatalytic reaction process. That is, the amount of active oxygen derived from the TiO 2 photocatalytic reaction can be determined from the time-resolved chemiluminescence signal. As a spectroscope used in the present invention, for example, SP-308 of Nippon Rover Co., Ltd. and PMT can be exemplified by 928 of Hamamatsu Hotnix. A filter that allows chemiluminescence of luminol can be used instead of the spectroscope.

なお、本実施形態では分光器を用いた例を示したが、分光器を介在させず直接レンズ系4b、4cを経由して直接光電子増倍管に導入することも可能である。   In the present embodiment, an example using a spectroscope has been shown, but it is also possible to introduce it directly into the photomultiplier tube via the lens systems 4b and 4c without interposing the spectroscope.

以下に、光触媒活性評価装置1を用いて、異なるTiO2光触媒水溶液の光触媒活性を評価した結果について説明する。TiO2粉末0.25g/lにルミノール1.5×10−4Mを添加した水溶液を、1cm×1cmの石英製光学セルに入れ、試料として用いた。評価対象のTiO2は、(1)P25、(2)和光1、(3)和光2(2は1と異なるロット番号)、(4)MERCK、(5)FT2000(石原産業)、(6)FT3000(石原産業)、(7)和光ルチル型、(8)ST21(石原産業)の8種類である。光学セルにNd:Yagレーザーの第三高調波(355nm)を光触媒に照射し、時間分解化学発光信号強度を観察した。図2、3は、それぞれ1msと100μs以内の時間分解化学発光信号を示す。これらの図から明らかなように、TiO2ごとにその光触媒特性が異なるため、発生する活性酸素の濃度あるいは量も異なり、その結果、時間分解化学発光信号強度も異なることが分かる。Below, the result of having evaluated the photocatalytic activity of different TiO2 photocatalyst aqueous solution using the photocatalytic activity evaluation apparatus 1 is demonstrated. An aqueous solution obtained by adding luminol 1.5 × 10 −4 M to 0.25 g / l of TiO 2 powder was put into a 1 cm × 1 cm quartz optical cell and used as a sample. The evaluation target TiO2 is (1) P25, (2) Wako 1, (3) Wako 2 (2 is a lot number different from 1), (4) MERCK, (5) FT2000 (Ishihara Sangyo), (6) FT3000 (Ishihara Sangyo), (7) Wako rutile type, (8) ST21 (Ishihara Sangyo). The optical cell was irradiated with the third harmonic (355 nm) of Nd: Yag laser on the photocatalyst, and the time-resolved chemiluminescence signal intensity was observed. 2 and 3 show time-resolved chemiluminescence signals within 1 ms and 100 μs, respectively. As can be seen from these figures, since the photocatalytic properties of each TiO 2 are different, the concentration or amount of the generated active oxygen is different, and as a result, the time-resolved chemiluminescence signal intensity is also different.

さらに、本発明による評価方法による光触媒活性と有機物分解性との相関を調べるため、以下の試験を行った。TiO2粉末0.25g/lに環境ホルモンであるビスフェノールA(40ppm)を添加した水溶液にNd:Yagレーザーの第三高調波(355nm)を光触媒に照射し、光触媒反応による分解を一定時間(30分)行った。評価対象のTiO2は、実施例1と同じく、(1)P25、(2)和光1、(3)和光2(2は1と異なるロット番号)、(4)MERCK、(5)FT2000(石原産業)、(6)FT3000(石原産業)、(7)和光ルチル型、(8)ST21(石原産業)の8種類である。   Furthermore, in order to investigate the correlation between the photocatalytic activity and the organic matter decomposability by the evaluation method according to the present invention, the following tests were conducted. The third harmonic (355 nm) of Nd: Yag laser is irradiated to an aqueous solution in which bisphenol A (40 ppm), an environmental hormone, is added to 0.25 g / l of TiO2 powder, and decomposition by the photocatalytic reaction is performed for a certain time (30 minutes) )went. TiO2 to be evaluated is the same as in Example 1, (1) P25, (2) Wako 1, (3) Wako 2 (2 is a lot number different from 1), (4) MERCK, (5) FT2000 (Ishihara Sangyo) ), (6) FT3000 (Ishihara Sangyo), (7) Wako rutile type, (8) ST21 (Ishihara Sangyo).

その後、残留ビスフェノールAを高速液体クロマトグラフィー(HPLC)で測定し、各種TiO2の光触媒反応によるビスフェノールAの分解率を得た。図4は、同分解率を横軸にとり、図2中の時間分解化学発光信号の積分値(対数)を縦軸にとって、各TiO2の値をプロットしたものである。同図から明らかなように、時間分解化学発光信号の積分値が大きいほど、ビスフェノールAの光触媒反応による分解率も大きいことが分かる。このことは、時間分解化学発光信号強度はHPLCで得た分解率と相関関係があることを示している。従って、本発明による時間分解化学発光信号強度測定がTiO2の有機物に対する光触媒性能評価に利用できることを意味している。   Thereafter, residual bisphenol A was measured by high performance liquid chromatography (HPLC) to obtain a decomposition rate of bisphenol A by photocatalytic reaction of various TiO 2. FIG. 4 plots the value of each TiO2 with the decomposition rate on the horizontal axis and the integrated value (logarithm) of the time-resolved chemiluminescence signal in FIG. 2 on the vertical axis. As is apparent from the figure, it can be seen that the larger the integrated value of the time-resolved chemiluminescence signal, the greater the decomposition rate of bisphenol A due to the photocatalytic reaction. This indicates that the time-resolved chemiluminescence signal intensity is correlated with the degradation rate obtained by HPLC. Therefore, it means that the time-resolved chemiluminescence signal intensity measurement according to the present invention can be used for evaluating the photocatalytic performance of TiO 2 organic matter.

本発明は、金属酸化物半導体の光触媒活性及び有機物に対する分解特性の評価手段として、広く利用可能である。   The present invention can be widely used as a means for evaluating the photocatalytic activity of metal oxide semiconductors and the decomposition characteristics of organic substances.

光触媒活性評価装置1の全体構成を示す図である。It is a figure which shows the whole structure of the photocatalytic activity evaluation apparatus. 異なるTiO2光触媒水溶液の1.25ms以内の時間分解化学発光信号強度を示す図である。It is a figure which shows the time-resolved chemiluminescence signal intensity | strength within 1.25 ms of different TiO2 photocatalyst aqueous solution. 異なるTiO2光触媒水溶液の125μs以内の時間分解化学発光信号強度を示す図である。It is a figure which shows the time-resolved chemiluminescence signal intensity within 125 microseconds of different TiO2 photocatalyst aqueous solution. 時間分解化学発光信号強度とビスフェノールAの光触媒分解率との相関を示す図である。It is a figure which shows the correlation with time-resolved chemiluminescence signal intensity | strength and the photocatalytic degradation rate of bisphenol A. 請求項11に係る発明の作用を概念的に示した図である。It is the figure which showed notionally the effect | action of the invention which concerns on Claim 11.

符号の説明Explanation of symbols

1 光触媒活性評価装置
2 レーザー照射装置
3 分散プリズム
4a〜4c 集光レンズ
5 光学セル
6 ノッチフィルタ
7 分光器
8 光電子増倍管(PMT)
9 デジタルオシロスコープ
DESCRIPTION OF SYMBOLS 1 Photocatalytic activity evaluation apparatus 2 Laser irradiation apparatus 3 Dispersion prism 4a-4c Condensing lens 5 Optical cell 6 Notch filter 7 Spectrometer 8 Photomultiplier tube (PMT)
9 Digital oscilloscope

Claims (9)

金属酸化物半導体とルミノールを含む溶液に波長400nm以下のパルスレーザーを照射し、発生する活性酸素種とルミノールとの反応に伴うレーザー照射後10ms以内の時間分解化学発光信号強度に基づいて、短寿命活性酸素であるOHラジカルの発生量を求めることにより光触媒活性を評価することを特徴とする金属酸化物半導体の光触媒活性評価方法。Short life based on time-resolved chemiluminescence signal intensity within 10 ms after laser irradiation with irradiation of pulsed laser with wavelength of 400 nm or less to solution containing metal oxide semiconductor and luminol A method for evaluating the photocatalytic activity of a metal oxide semiconductor, wherein the photocatalytic activity is evaluated by determining the amount of OH radicals that are active oxygen. 前記金属酸化物半導体が、二酸化チタン(TiO2)又は酸化亜鉛(ZnO)のいずれかであることを特徴とする請求項に記載の光触媒活性評価方法。2. The photocatalytic activity evaluation method according to claim 1 , wherein the metal oxide semiconductor is either titanium dioxide (TiO2) or zinc oxide (ZnO). 前記化学発光信号強度の最大値に基づいて光触媒活性度を評価することを特徴とする請求項1又は2に記載の光触媒活性評価方法。The photocatalytic activity evaluation method according to claim 1 or 2 , wherein the photocatalytic activity is evaluated based on the maximum value of the chemiluminescence signal intensity. 前記化学発光信号強度の30μs〜10msまでの積分値に基づいて光触媒活性度を評価することを特徴とする請求項1又は2に記載の光触媒活性評価方法。The photocatalytic activity evaluation method according to claim 1 or 2 , wherein the photocatalytic activity is evaluated based on an integrated value of the chemiluminescence signal intensity of 30 µs to 10 ms. 評価対象の金属酸化物半導体とルミノールを含む溶液を収めた光学セルと、該光学セルに波長400nm以下のパルスレーザーを照射する手段と、パルスレーザー照射による前記溶液からの発光を検出してレーザー照射後10ms以内の化学発光信号強度を取得する化学発光信号強度取得手段と、化学発光信号強度に基づいてOHラジカル発生量を演算する手段と、を備えて成ることを特徴とする光触媒活性評価装置。An optical cell containing a solution containing a metal oxide semiconductor to be evaluated and luminol, means for irradiating the optical cell with a pulse laser having a wavelength of 400 nm or less, and detecting the light emitted from the solution by the pulse laser irradiation to irradiate the laser A photocatalytic activity evaluation apparatus comprising: a chemiluminescence signal intensity acquisition means for acquiring a chemiluminescence signal intensity within 10 ms later ; and a means for calculating an OH radical generation amount based on the chemiluminescence signal intensity. 前記光学セルと前記化学発光信号強度取得手段の経路中に、さらに、レーザー散乱光除去手段を備えて成ることを特徴とする請求項に記載の光触媒活性評価装置。6. The photocatalytic activity evaluation apparatus according to claim 5 , further comprising a laser scattered light removing unit in a path between the optical cell and the chemiluminescence signal intensity obtaining unit. 前記レーザー散乱光除去手段が、ノッチフィルタであることを特徴とする請求項に記載の光触媒活性評価装置。The photocatalytic activity evaluation apparatus according to claim 6 , wherein the laser scattered light removing means is a notch filter. 前記光学セルと発光検出手段の経路中に、さらに分光器又はフィルタを配置して成ることを特徴とする請求項乃至に記載の光触媒活性評価装置。Wherein in the path of the optical cell and the light emitting detection means, the photocatalytic activity evaluation device according to claim 5 to 7, characterized by comprising placing a further spectrometer or filter. 有機物とルミノールとを含む溶液にパルスレーザーを照射し、有機物の光触媒分解反応に伴うルミノールの時間分解化学発光信号強度を求め、このデータと請求項1乃至の方法による発生活性酸素種とルミノールとの反応に伴う時間分解化学発光信号強度とを比較することにより、前記金属酸化物半導体の前記有機物に対する分解活性を評価することを特徴とする光触媒活性評価方法。A solution containing an organic substance and luminol is irradiated with a pulse laser to determine a time-resolved chemiluminescence signal intensity of luminol accompanying a photocatalytic decomposition reaction of the organic substance, and this data and the generated reactive oxygen species and luminol by the method of claims 1 to 4 are obtained. A photocatalytic activity evaluation method characterized by evaluating the decomposition activity of the metal oxide semiconductor with respect to the organic matter by comparing the time-resolved chemiluminescence signal intensity associated with the reaction of.
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