堀越 智

The mechanism of photo-oxidation of the water-soluble polyvinylpyrrolidone (PVP) having a pendant five-membered lactam ring is complicated by the manner by which the macromolecule adsorbs on the TiO2 particle surface in a heterogeneous dispersion. Experimental results and computer simulation of the initial process(es) infer three major steps for the photodegradation of the PVP structure. The first step is adsorption (or coagulation) of PVP on TiO2 particles as evidenced by the size distribution of TiO2 particles by dynamic light-scattering and by the electric charge on the TiO2 particle surface assayed by zeta -potential measurements. Molecular orbital simulations of initial processes were calculated at the AMI level using the MOPAC system available in the CAChe package. The second step, namely attack of PVP by (OH)-O-. and/or (OOH)-O-. radicals, involves cleavage of the PVP main chain and opening of the lactam ring in the PVP structure probed by temporal UV spectral changes and by a decrease of the molecular weight using gel permeation chromatographic methods. Additional details of the photo-oxidation mode of the lactam ring was examined by a detailed examination of the photo-oxidation of the model compound 2-pyrrolidone to ascertain formation of (OH)-O-. radical adducts, opening of the lactam ring, and identification of intermediates by HPLC, and C-13- and H-1-NMR methods. The fnal major step in the mechanism involves generation and subsequent conversion of the primary amine (methylamine from opening of the lactam ring) to yield ultimately NH4+ and NO3- ions, and conversion of the propanoic acid to acetic and formic acids and then to CO2. The effects of the extent of polymerization and variation in light intensity were examined using PVP samples having different hardness factors (hf) of 15 and 30, and different light intensities (namely, 1, 2, 3 and 4 mW cm(-2)), respectively. (C) 2001 Elsevier Science B.V. All rights reserved.

Sodium benzene sulfonate (BS) was decomposed in aqueous TiO(2) dispersions under highly concentrated solar light illumination to examine the photocatalytic characteristics of a parabolic round concentrator (PRC) reactor to degrade the pollutant without visible light absorption. The effects of such operational parameters as initial concentration, volume of the aqueous BS solution, oxygen purging, and TiO(2) loading on the kinetics of decomposition of BS were investigated. An effective photodegradation necessitates a suitable combination of initial volume and concentration of BS solution. Relative to atmospheric air, oxygen purging significantly accelerates the degradation process at high initial concentrations of BS (0.40 mM or 1.0 mM). Optimal TiO(2) loading was 9 g l(-1), greater than previously reported. Elimination of TOC (total organic carbon) followed pseudo first-order kinetics in the initial stages of the photodegradation process. The relative photonic efficiency for the photodegradation of BS is zeta (rel) = 1.0. (C) 2001 Elsevier Science Ltd. All rights reserved.

In this study we focus on elucidating the mechanism of the photocatalyzed transformation of the primary, secondary and tertiary amines found in ethanolamine, diethanolamine and triethanolamine when present in illuminated aqueous titania dispersions. Photodecomposition of these ethanolamines leads to the evolution of CO2 through prior formation of various intermediate species. Ammonium (NH4+) and nitrate ions (NO3-) are the ultimate products formed in the photoconversion of the amine nitrogen atoms, with NH4+ cations produced in greater quantity than NO3- anions for all three ethanolamines. Photooxidation of triethanolamine yields various intermediates, including a 3-pyrrolidone derivative, diethanolamine, and then ethanolamine, before complete mineralization occurs. The nature of the initial steps in the photodegradation was predicted by computer-aided molecular orbital (MO) calculations of point charges, and by frontier electron densities of all atoms in the ethanolamine structures.

This study reports on a comparative assessment of the efficiencies of TiO2/SnO2-doped OTE thin film electrodes fabricated by three different deposition methods. Process efficiencies, as measured by the kinetics of degradation, were examined by monitoring the photo-oxidative fate of two test substrates, namely the anionic surfactant sodium dodecylbenzenesulfonate (DBS) and the model compound sodium benzenesulfonate (BS). Methods chosen to fabricate the TiO2/OTE electrodes comprised (i) pulsed laser deposition, (ii) deposition of a TiO2 paste on the OTE plate, and (iii) sol-gel deposition. Both DBS and BS are readily photo-oxidized and, under our conditions, were partially mineralized to CO2 with the process being made particularly more efficient when the TiO2/OTE electrodes were anodically biased at +0.3 V, which generated a photocurrent during the photoelectrolysis. The sol-gel {C} and anatase {B1} electrodes proved especially useful under the +0.3 V bias. In the absence of any bias, however, DBS photodegraded faster on the TiO2-pasted electrode. Under otherwise similar conditions, the pulsed laser rutile TiO2/OTE electrode showed very little photoactivity. Some of the characteristics of the TiO2 film, such as the TiO2 crystalline form, film thickness, surface roughness, and film transparency appear to have some effect on the overall photodegradative process efficiency. (C) 2001 Elsevier Science B.V. All rights reserved.

In this study we focus on elucidating the mechanism of the photocatalyzed transformation of the primary, secondary and tertiary amines found in ethanolamine, diethanolamine and triethanolamine when present in illuminated aqueous titania dispersions. Photodecomposition of these ethanolamines leads to the evolution of CO2 through prior formation of various intermediate species. Ammonium (NH4 +) and nitrate ions (NO3 -) are the ultimate products formed in the photoconversion of the amine nitrogen atoms, with NH4 + cations produced in greater quantity than NO3 - anions for all three ethanolamines. Photooxidation of triethanolamine yields various intermediates, including a 3-pyrrolidone derivative, diethanolamine, and then ethanolamine, before complete mineralization occurs. The nature of the initial steps in the photodegradation was predicted by computer-aided molecular orbital (MO) calculations of point charges, and by frontier electron densities of all atoms in the ethanolamine structures.

The photocatalytic oxidation of oxalyldihydrazide, N, N'-bis(hydrazocarbonyl)hydrazide, N, N'-bis(ethoxycarbonyl)hydrazide, malonyldihydrazide, N-malonyl-bis[(N'-ethoxycarbonyl)hydrazide] was examined in aqueous TiO2 dispersions under UV illumination. The photomineralization of nitrogen and carbon atoms in the substrates into N-2 gas, NH4+ (and/or NO3-) ions, and CO2 gas was determined by HPLC and GC analysis. The formation of carboxylic acid intermediates also occurred in the photooxidation process. The photocatalytic mechanism is discussed on the basis of the experimental results, and with molecular orbital (MO) simulation of frontier electron density and point charge. Substrate carbonyl groups readily adsorb on the TiO2 surface, and the bonds between carbonyl group carbon atoms and adjacent hydrate group nitrogen atoms are cleaved predominantly in the initial photooxidation process. The hydrate groups were photoconverted mainly into N-2 gas (in mineralization yields above 70%) and partially to NH4+ ions (below 10%). The formation of NO3- ions was scarcely recognized. (C) 2000 Elsevier Science Ltd. All rights reserved.

The photocatalytic oxidation of oxalyldihydrazide, N, N'-bis(hydrazocarbonyl)hydrazide, N, N'-bis(ethoxycarbonyl)hydrazide, malonyldihydrazide, N-malonyl-bis[(N'-ethoxycarbonyl)hydrazide] was examined in aqueous TiO2 dispersions under UV illumination. The photomineralization of nitrogen and carbon atoms in the substrates into N-2 gas, NH4+ (and/or NO3-) ions, and CO2 gas was determined by HPLC and GC analysis. The formation of carboxylic acid intermediates also occurred in the photooxidation process. The photocatalytic mechanism is discussed on the basis of the experimental results, and with molecular orbital (MO) simulation of frontier electron density and point charge. Substrate carbonyl groups readily adsorb on the TiO2 surface, and the bonds between carbonyl group carbon atoms and adjacent hydrate group nitrogen atoms are cleaved predominantly in the initial photooxidation process. The hydrate groups were photoconverted mainly into N-2 gas (in mineralization yields above 70%) and partially to NH4+ ions (below 10%). The formation of NO3- ions was scarcely recognized. (C) 2000 Elsevier Science Ltd. All rights reserved.

Visible light-induced photocatalytic oxidation of the dye alizarin red (AR) has been examined in TiO2 aqueous dispersions. The ESR spin-trapping technique was used to detect active oxygen radicals formed during in situ visible irradiation of AR/TiO2 dispersions. Evidence for the production of superoxide (O-2(.-) or HOO.) (formed in the reduction of O-2) and hydroxyl radicals ((OH)-O-.) (formed by a multistep reduction) in the initial photoexcitation stage is presented. Meanwhile, the pathway of the photooxidation of AR is theoretically predicted on the basis of molecular orbital (MO) calculations by frontier electron densities and point charges on all the individual atoms of the dye. The relatively high negative point charges on the sulfonic oxygens lead to a strong adsorption of the dye onto the TiO2 particle surface through the sulfonate function. The position of the dye molecule attacked by the active oxygen species (e.g. O2(.-) or HOO. radicals) and/or O-2 is correlated with frontier electron densities, there is a perfect agreement between MO calculations and the results of experiments. A plausible mechanism of photooxidation under visible irradiation is discussed. (C) 2000 Elsevier Science B.V. All rights reserved.

河川へ廃棄された非イオン界面活性剤であるノニルフェノールポリエトキシレート (NPE) は, 生分解により毒性が強く, 水に難溶性の内分泌かく乱物質ノニルフェノール (NP) 中間生成物が生成する。本研究では二酸化チタン光触媒を用いたNPEやNPの光酸化メカニズムについて研究を行った。これらの光分解における表面張力の変化, TOC変化, CO₂ガスの発生量, FT-IR, NMR, GC-MS, 光散乱によるTiO₂粒子への吸着状態などを検討した。分子軌道法を用いて, ^・OHラジカルの攻撃位置やTiO₂表面への吸着シミュレーションを行い, 実験結果と比較した。TiO₂光触媒によりNPEやNPなどが不均一水溶液分散系で分解できることが分かった。またそのメカニズムについても考察した。

The mechanistic sequence(s) in the TiO2-photocatalytic oxidation of constituent pyrimidine and purine bases in nucleic acids is examined theoretically by molecular orbital calculations of frontier electron densities and point charges on all atoms, and experimentally by UV-Vis spectroscopy and gas chromatography to assess how the chemical structure of the bases affects their photocatalyzed mineralization. Rates of formation of NH4+ and NO3- ions in the pyrimidine bases are closely dependent on the existence of the carbonyl and amino groups; for example, formation of NO3- ions is faster than formation of NH4+ ions for uracil (Ura) and thymine (Thy) having the carbonyl function. By contrast, NH4+ ions are produced faster than NO3- ions in the case of cytosine (Cyt) which possesses a primary amine function. In comparison with uric acid, which has no amino group, the photocatalyzed mineralization of the purine bases adenine (Ade) and guanine (Gua) generates a greater quantity of NH4+ ions than NO3- ions, in the initial stages. In nearly all cases examined, formation of NO3- ions takes place only after an induction period and originates mostly from the ring nitrogen atoms of the bases. (C) 1999 Elsevier Science S.A. All rights reserved.

The photoelectrical degradation of the amino acids L-aspartic acid (L-Asp), L-glutamic acid (L-Glu), L-leucine (L-Leu), L-alpha-alanine (L-alpha-Ala) and beta-alanine (beta-Ala) was examined on TiO2/OTE electrodes prepared by a pulse laser deposition method. The disappearance of amino acids and their mineralization into CO2 were determined with and without an applied anionic bias of 0.3 V. The generation of photocurrent was also measured during the photoelectrical degradation of substrates on the TiO2/OTE electrode assembly considering it as a possible type of solar cell. The relationship between the photoelectrodegradation rate, the photocurrent and the structure of the amino acids was established.

半導体光触媒TiO₂を用いたペプチド結合を有するドデカノイルアミド系非イオン界面活性剤の光酸化メカニズムについて研究した。C₁₂-モノエタノールアミドおよびC₁₂-ジエタノールアミドの光分解における表面張力の変化, CO₂ガスの発生量, カルボン酸中間体, NH₄⁺およびNO₃^-イオンの生成, 光散乱によるTiO₂粒子への吸着状態, ζ電位などを測定した。分子軌道法を用いて, OHラジカルの攻撃位置やTiO₂表面への吸着シミュレーションを行い, 実験結果と比較した。<BR>C₁₂-モノエタノールアミドおよびC₁₂-ジエタノールアミドの両者ともNO₃-イオンよりNH₄⁺の方が多く発生した。プラスに荷電したTiO₂表面へ活性剤中のマイナスに荷電した分子が吸着し, 活性剤分子中の電荷密度の高い位置にOHラジカルが攻撃しやすいことが分った。

The photoelectrical degradation of the amino acids L-aspartic acid (L-Asp), L-glutamic acid (L-Glu), L-leucine (L-Leu), L-alpha-alanine (L-alpha-Ala) and beta-alanine (beta-Ala) was examined on TiO2/OTE electrodes prepared by a pulse laser deposition method. The disappearance of amino acids and their mineralization into CO2 were determined with and without an applied anionic bias of 0.3 V. The generation of photocurrent was also measured during the photoelectrical degradation of substrates on the TiO2/OTE electrode assembly considering it as a possible type of solar cell. The relationship between the photoelectrodegradation rate, the photocurrent and the structure of the amino acids was established.

The photooxidative degradation of a TiO2-blended poly(vinyl chloride) (PVC) film and other PVC specimens was carried out under UV light and under solar exposure to test the feasibility that such polymeric materials can be mineralized. The effects of the degree of polymerization and the presence of a plasticizer (o-dioctyl phthalate DOP) in the PVC on the photooxidation process were examined by scanning electron microscopy (SEM), by X-ray photoelectron spectroscopy (XPS), by gel permeation chromatography, and by gas chromatography for CO2 evolution. The TiO2-blended PVC thin film is more easily decomposed than PVC particles (or film) alone in a TiO2 particulate dispersion. The collapse phenomena of polymeric films are closely dependent on the photodegradation rate of DOP in the PVC film. Ames mutagenic assays for the photodegraded solution in aqueous TiO2/PVC dispersions showed a slight mutagenic activity in TA98 without S9 mix for products formed during the photodegradative oxidation.

The photooxidative degradation of a TiO2-blended poly(vinyl chloride) (PVC) film and other PVC specimens was carried out under UV light and under solar exposure to test the feasibility that such polymeric materials can be mineralized. The effects of the degree of polymerization and the presence of a plasticizer (o-dioctyl phthalate; DOP) in the PVC on the photooxidation process were examined by scanning electron microscopy (SEM), by X-ray photoelectron spectroscopy (XPS), by gel permeation chromatography, and by gas chromatography for CO;, evolution. The TiO2-blended PVC thin film is more easily decomposed than PVC particles (or film) alone in a TiO2 particulate dispersion. The collapse phenomena of polymeric films are closely dependent on the photodegradation rate of DOP in the PVC film. Ames mutagenic assays for the photodegraded solution in aqueous TiO2/PVC dispersions showed a slight mutagenic activity in TA98 without S9 mix for products formed during the photodegradative oxidation.

The pathway to the photomineralization of the three amino acids L-serine (L-Ser), L-phenylalanine (L-Phe) and L-a-alanine (L-Ala) is described experimentally on the basis of CO2 evolution and conversion of the amino group to NH4+ and NO3- ions, and theoretically on the basis of molecular orbital calculations to define frontier electron densities and point charges on all the individual atoms. The relatively high negative point charges on the carboxylate oxygens are consistent with adsorption of the amino acids to the TiO2 particle surface through the carboxylate function. Mineralization to carbon dioxide is complete for L-Ser (similar to 98%) and nearly so for L-Ala (similar to 90%), whereas for L-Phe the extent of mineralization is 59% corresponding to the total photooxidation of the phenyl ring carbons; for the amine function the extent of conversion is 87% for L-Ser, 97% for L-Ala and 91% for L-Phe. Relative formation yields of NH4+ and NO3- ions depend on the structural fragment R attached to the a-amino carboxylic acid functions, R-CH(NH2)COOH. Primary attack of the amino acids by the (OH)-O-. radical is correlated with the frontier electron densities. Ammonia is formed through a photoreductive step by electron attachment onto the zwitterionic form of the amino acids, whereas nitrate is produced through a photooxidative step implicating a very tortuous series of events. (C) 1998 Elsevier Science S.A. All rights reserved.

The pathway to the photomineralization of the three amino acids L-serine (L-Ser), L-phenylalanine (L-Phe) and L-a-alanine (L-Ala) is described experimentally on the basis of CO2 evolution and conversion of the amino group to NH4+ and NO3- ions, and theoretically on the basis of molecular orbital calculations to define frontier electron densities and point charges on all the individual atoms. The relatively high negative point charges on the carboxylate oxygens are consistent with adsorption of the amino acids to the TiO2 particle surface through the carboxylate function. Mineralization to carbon dioxide is complete for L-Ser (similar to 98%) and nearly so for L-Ala (similar to 90%), whereas for L-Phe the extent of mineralization is 59% corresponding to the total photooxidation of the phenyl ring carbons; for the amine function the extent of conversion is 87% for L-Ser, 97% for L-Ala and 91% for L-Phe. Relative formation yields of NH4+ and NO3- ions depend on the structural fragment R attached to the a-amino carboxylic acid functions, R-CH(NH2)COOH. Primary attack of the amino acids by the (OH)-O-. radical is correlated with the frontier electron densities. Ammonia is formed through a photoreductive step by electron attachment onto the zwitterionic form of the amino acids, whereas nitrate is produced through a photooxidative step implicating a very tortuous series of events. (C) 1998 Elsevier Science S.A. All rights reserved.

The fate of DNA, RNA and their pyrimidine and purine bases was examined on exposure to WA and UVB radiation in the presence of a physical sunscreen agent (TiO(2), anatase/rutile particles) to assess the potential damage that such an agent may cause on contact with such substrates. DNA and RNA were partially decomposed and the bases were converted to carbon dioxide (nitrogen atoms to ammonia and nitrate ions) in a Pyrex reactor under conditions simulating UVA and UVB sunlight. The physical and chemical damage inflicted on DNA and RNA was also confirmed by scanning electron microscopy and gel permeation chromatography. (C) 1997 Elsevier Science S.A.

The fate of DNA, RNA and their pyrimidine and purine bases was examined on exposure to WA and UVB radiation in the presence of a physical sunscreen agent (TiO(2), anatase/rutile particles) to assess the potential damage that such an agent may cause on contact with such substrates. DNA and RNA were partially decomposed and the bases were converted to carbon dioxide (nitrogen atoms to ammonia and nitrate ions) in a Pyrex reactor under conditions simulating UVA and UVB sunlight. The physical and chemical damage inflicted on DNA and RNA was also confirmed by scanning electron microscopy and gel permeation chromatography. (C) 1997 Elsevier Science S.A.

Titanium dioxide (TiO2) has been noted (US Federal Register, 43FR38206, 25 August 1978) to be a safe physical sunscreen because it reflects and scatters UVB and UVA in sunlight. However, TiO2 absorbs about 70% of incident UV, and in aqueous environments this leads to the generation of hydroxyl radicals which can initiate oxidations, Using chemical methods, we show that all sunscreen TiO2 samples tested catalyse the photo-oxidation of a representative organic substrate (phenol), We also show that sunlight-illuminated TiO2 catalyses DNA damage both in vitro and in human cells, These results may be relevant to the overall effects of sunscreens. (C) 1997 Federation of European Biochemical Societies.

Titanium dioxide (TiO2) has been noted (US Federal Register, 43FR38206, 25 August 1978) to be a safe physical sunscreen because it reflects and scatters UVB and UVA in sunlight. However, TiO2 absorbs about 70% of incident UV, and in aqueous environments this leads to the generation of hydroxyl radicals which can initiate oxidations, Using chemical methods, we show that all sunscreen TiO2 samples tested catalyse the photo-oxidation of a representative organic substrate (phenol), We also show that sunlight-illuminated TiO2 catalyses DNA damage both in vitro and in human cells, These results may be relevant to the overall effects of sunscreens. (C) 1997 Federation of European Biochemical Societies.

The photoelectrochemical degradation of amino acids and derivatives such as glutamic acid, glutamine, glutaric acid, lysine, beta-alanine, 8-aminooctanoic acid and phenylalanine has been examined on an irradiated TiO2/OTE particulate film electrode. The photooxidative disappearance of the substrates ultimately transforms the nitrogen into NO3- and NH3 (as ammonium ions under our conditions), whereas the carbonaceous residues are converted into CO2. Variations in photocurrent were observed during the temporal course of the photodegradative process. The rates of conversion and the quantity of degraded products depend on the external applied bias and appear to be closely related to the molecular structure of the substrates. A photoelectrochemical degradative pathway is discussed briefly on the basis of the experimental observations. (C) 1997 Elsevier Science S.A.

The photoelectrochemical degradation of amino acids and derivatives such as glutamic acid, glutamine, glutaric acid, lysine, beta-alanine, 8-aminooctanoic acid and phenylalanine has been examined on an irradiated TiO2/OTE particulate film electrode. The photooxidative disappearance of the substrates ultimately transforms the nitrogen into NO3- and NH3 (as ammonium ions under our conditions), whereas the carbonaceous residues are converted into CO2. Variations in photocurrent were observed during the temporal course of the photodegradative process. The rates of conversion and the quantity of degraded products depend on the external applied bias and appear to be closely related to the molecular structure of the substrates. A photoelectrochemical degradative pathway is discussed briefly on the basis of the experimental observations. (C) 1997 Elsevier Science S.A.

The fate of nitrogen in various amino acids was examined following their photooxidative (and/or reductive) transformation catalyzed by UV-A and UV-B illuminated aqueous TiO2 dispersions. The nitrogens in the amino acids are photoconverted predominantly into NH, (analyzed as NH4+) and to a lesser extent into NO3- ions; NH4+/NO3- ratios span the range 3-12 after ca. 8 h irradiation. Extensive evolution of CO2 is also observed; in some cases it is quantitative. Variations in the NH4+/NO3- ratio in the transformation of amino acids are dependent on the substrates molecular structure. Some of the steps in an otherwise complex mechanism of the heterogeneous photocatalyzedmineralization are described. (C) 1997 Elsevier Science S.A.

The fate of nitrogen in various amino acids was examined following their photooxidative (and/or reductive) transformation catalyzed by UV-A and UV-B illuminated aqueous TiO2 dispersions. The nitrogens in the amino acids are photoconverted predominantly into NH, (analyzed as NH4+) and to a lesser extent into NO3- ions; NH4+/NO3- ratios span the range 3-12 after ca. 8 h irradiation. Extensive evolution of CO2 is also observed; in some cases it is quantitative. Variations in the NH4+/NO3- ratio in the transformation of amino acids are dependent on the substrates molecular structure. Some of the steps in an otherwise complex mechanism of the heterogeneous photocatalyzedmineralization are described. (C) 1997 Elsevier Science S.A.

The photo-oxidative degradation of sodium benzene sulfonate, 2-phenoxyethanol, ethyleneglycol, diethyleneglycol, acetic acid and formic acid, was examined on a TiO2 particulate film immobilized on a transparent conductive oxide (TCO) glass electrode assembly. The photocurrents generated during the photodegradation of these organic compounds were monitored. Formation of intermediate species (acetic acid and formic acid) during the temporal course of the photo-oxidative process(es) appears to have a direct effect on the photocurrents.

The photo-oxidative degradation of sodium benzene sulfonate, 2-phenoxyethanol, ethyleneglycol, diethyleneglycol, acetic acid and formic acid, was examined on a TiO2 particulate film immobilized on a transparent conductive oxide (TCO) glass electrode assembly. The photocurrents generated during the photodegradation of these organic compounds were monitored. Formation of intermediate species (acetic acid and formic acid) during the temporal course of the photo-oxidative process(es) appears to have a direct effect on the photocurrents.

The photocatalyzed oxidative decompositions of solid particles of polyvinylchloride (PVC; size about 100 to 200 mu m), of the polyvinylidene chloride copolymer (95% PVC/5% PVLC; size similar to 400-600 mu m), and a PVC film have been examined in suspensions of titania and zinc oxide illuminated by UV light and/or by natural sunlight. Dechlorination and evolution of carbon dioxide were monitored, the latter occurring by the intermediacy of acetic and formic acids. The photodegradation of polymer specimens was enhanced in TiO2/water media by such added oxidants as hydrogen peroxide and potassium persulfate. Photocorrosion of these particulates was also examined by scanning electron microscopy. (C) 1996 John Wiley & Sons, Inc.

The photocatalyzed oxidative decompositions of solid particles of polyvinylchloride (PVC; size about 100 to 200 mu m), of the polyvinylidene chloride copolymer (95% PVC/5% PVLC; size similar to 400-600 mu m), and a PVC film have been examined in suspensions of titania and zinc oxide illuminated by UV light and/or by natural sunlight. Dechlorination and evolution of carbon dioxide were monitored, the latter occurring by the intermediacy of acetic and formic acids. The photodegradation of polymer specimens was enhanced in TiO2/water media by such added oxidants as hydrogen peroxide and potassium persulfate. Photocorrosion of these particulates was also examined by scanning electron microscopy. (C) 1996 John Wiley & Sons, Inc.

陰イオン系 (DBS), 陽イオン系 (CTAB, BTDACC₁₂-PC), 非イオン系 (C₁₂E₅, N-DHA) および両性系 (C₁₂-betaine, C₁₂-amidobetaine, C₁₂-HAA) 各界面活性剤が紫外線照射下, 半導体光触媒分散系中で光分解した。化学構造に対する光分解速度の依存性を全有機炭素 (TOC) 量から検討した。ZnO, WO3, TiO₂ (アナターゼまたはルチル), TiO₂ (Uv-100), TiO₂ (T-805) の触媒の光触媒効果の違いを検討した。 TiO₂ (アナターゼ) とZnOは優れた触媒効果を示した。各界面活性剤が酸化されCO₂ガスを生じるので, TOC は光照射時間とともに減少する。光照射をせず超音波後のToc値は出発原液よりも小さい。これはTiO₂ 表面に活性剤が吸着するからである。陰イオン系活性剤の光分解速度は非イオン, 陽イオンおよび両性界面活性剤より早く, 高濃度は光分解速度が低下する。コロイド状TiO₂とbenzene sulfonate (BS) の系でのレーザーフラッシュフォトリシスの測定結果より, 界面活性剤の分解は電荷移動媒体の捕捉と関連しており, 安定状態のBS⁺・カチオンラジカルまたはBSのベンゼン環の・OHラジカル付加体を生成している。

陰イオン系 (DBS), 陽イオン系 (CTAB, BTDACC₁₂-PC), 非イオン系 (C₁₂E₅, N-DHA) および両性系 (C₁₂-betaine, C₁₂-amidobetaine, C₁₂-HAA) 各界面活性剤が紫外線照射下, 半導体光触媒分散系中で光分解した。化学構造に対する光分解速度の依存性を全有機炭素 (TOC) 量から検討した。ZnO, WO3, TiO₂ (アナターゼまたはルチル), TiO₂ (Uv-100), TiO₂ (T-805) の触媒の光触媒効果の違いを検討した。 TiO₂ (アナターゼ) とZnOは優れた触媒効果を示した。各界面活性剤が酸化されCO₂ガスを生じるので, TOC は光照射時間とともに減少する。光照射をせず超音波後のToc値は出発原液よりも小さい。これはTiO₂ 表面に活性剤が吸着するからである。陰イオン系活性剤の光分解速度は非イオン, 陽イオンおよび両性界面活性剤より早く, 高濃度は光分解速度が低下する。コロイド状TiO₂とbenzene sulfonate (BS) の系でのレーザーフラッシュフォトリシスの測定結果より, 界面活性剤の分解は電荷移動媒体の捕捉と関連しており, 安定状態のBS⁺・カチオンラジカルまたはBSのベンゼン環の・OHラジカル付加体を生成している。

The photooxidative degradation of an anionic surfactant, sodium dodecylbenzene sulfonate (DBS), has been examined on a TiO2 thin film immobilized onto a transparent semiconducting oxide (TCO support) electrode assembly. Some of the characteristics of this assembly have been explored. Changes in the rates of decomposition as a function of applied bias and as a function of the nature of the supporting electrolyte were surveyed. The efficiency of the photodegradation was governed by the electrode potential.

TiO₂ (アナターゼ型, ルチル型, 表面修飾型, 白金坦持型), ZnO, WO₃などのn型半導体による陰イオン性DBSおよび陽イオン性BDDAC界面活性剤の光分解の触媒効果を調べた。アナターゼ型TiO₂がルチル型TiO₂より光触媒能は強い。白金坦持TiO₂触媒はO₂のO₂^-への電子移動 (光還元) の抑制のため, アナターゼ型TiO₂より活性は低い。ZnOはDBSの光酸化に対して触媒活性が最も高く, 他の半導体触媒WO₃とMoSは触媒活性が低い。