京都大学 / 0048 / 新制・課程博士 / 博士(工学) / 甲第21119号 / 工博第4483号 / 新制||工||1697(附属図書館) / 京都大学大学院工学研究科物質エネルギー化学専攻 / (主査)教授 阿部 竜, 教授 安部 武志, 教授 陰山 洋 / 学位規則第4条第1項該当 / Doctor of Philosophy (Engineering) / Kyoto University / DGAM

This work presents a spectroscopic and theoretical study of several energy materials using synchrotron-based techniques. Two classes of materials are studied: solids that have reported photocatalytic properties, and lithium compounds that are thought to form during the cycling of modern battery electrodes. An overview of synchrotron soft X-ray spectroscopic techniques is presented, along with the theory and procedures associated with performing such measurements. These measurements are compared to density functional theory (DFT) calculations, as implemented by the WIEN2k package, along with a description of the DFT method. Calculated electronic structure is shown to be a useful aid in interpreting the results of X-ray emission and X-ray near-edge absorption measurements (XES and XANES), allowing conclusions about the physical structure and properties of the materials to be reached. Two photocatalytic systems are outlined, the first of which is a solid solution of GaN and ZnO (GaN:ZnO) that exhibits an unexpected reduction in band gap. By carefully comparing common hybridized features from O, N and Zn core emission lines, a binding energy picture of the valence and conduction bands of GaN:ZnO is constructed, allowing its band gap reduction to be described as a consequence of heterojunctions between predominantly GaN and ZnO regions within the solid solution. This description attempts to resolve controversy in the literature regarding the origin of the band gap reduction, as well as to rule out a hypothesized oxynitride superlattice structure as the explanation. The second photocatalytic system studied is a carbon nitride derivative, poly(triazine imide) (PTI) that displays high crystallinity and that could be very inexpensive to produce due to its elemental abundance. Through resonant excitation, two inequivalent N sites in PTI can be probed by X-ray emission spectroscopy, indicating the material is not a conjugated polymer like other reported carbon nitrides. The band gap of the system is observed to decrease in response to disordered Li loading, an e ect that is con rmed by DFT calculation. Several potential disorder models of the Li loading of PTI are investigated with DFT force minimization in order to choose a structural candidate capable of producing calculated X-ray spectra that agree with our measurements. The presented lithium study attempts to use a modern soft X-ray absorption facility to characterize the Li surface by-products inherent to the charge-discharge cycling of a battery electrode. A survey of potential Li compounds was performed using Li K-edge XANES will be compared to DFT calculations and X-ray Raman Scattering measurements performed by collaborators in the future. Correlating measurements of the survey compounds with charge-cycled electrode measurements will be an area for future work.

Plusieurs mécanismes de polymérisation radicalaire contrôlée (PRC) sous irradiation lumineuse ont récemment été développés. Ces approches offrent potentiellement de nombreux avantages, en permettant notamment d’introduire dans le mécanisme des PRCs certaines caractéristiques propres aux photopolymérisations, tels que les contrôles spatial et temporel de la réaction. Les travaux de thèse présentés dans ce manuscrit s’inscrivent dans ce contexte, en ayant pour objectif le développement et l’étude d’un nouveau mécanisme de polymérisation radicalaire par transfert d’atome (ATRP) photocatalysée. Après une étude bibliographique présentant l’état de l’art dans le domaine des PRCs sous irradiation lumineuse (chapitre 1), un complexe de bis(1,10-phenanthroline) cuivre (I) (Cu(I)) est utilisé comme catalyseur pour la synthèse de poly(méthacrylate de méthyle)s bien définis par ATRP menée sous l’irradiation d’une lampe LED bleue de faible intensité (chapitre 2). Le mécanisme proposé implique la formation de l’état excité Cu(I)* à partir de Cu(I) sous irradiation, suivie de sa désactivation oxydative par les composés bromés, générant les espèces actives propagatrices et la forme désactivante du complexe Cu(II). Le cycle catalytique est ensuite complété par l’ajout de triethylamine comme agent réducteur permettant la régénération in situ de la forme activante Cu(I) du complexe et conduisant ainsi à une polymérisation plus rapide. Le méthacrylate de glycidyle est ensuite considéré comme comonomère jouant simultanément le rôle d’un agent réducteur (chapitre 3). Des copolymères fonctionnels bien définis, avec une distribution contrôlée de groupes latéraux époxydes, sont ainsi synthétisés. Enfin, le mécanisme d’ATRP photocatalysé est amélioré en développant une procédure permettant la génération in situ de la forme activante Cu(I) en partant d’un complexe Cu(II) stable en présence d’air (chapitre 4). Le mécanisme ainsi développé présente une bonne tolérance à la présence d’oxygène ou d’inhibiteur dans le milieu réactionnel. Les effets de plusieurs paramètres (intensité lumineuse, concentration en ligand et nature du solvant ou du contre-ion) sont étudiés, suggérant un échange de ligand photo-induit comme processus photochimique additionnel impliqué dans le mécanisme d’ATRP photocatalysé étudié. / Several mechanisms of controlled radical polymerization (CRP) under light irradiation have been recently developed. These approaches offer potentially numerous advantages, enabling especially to introduce in the mechanism of CRPs some features characteristic of photopolymerizations, such as the spatial and temporal controls of the reaction. The PhD work presented in this manuscript comes in this framework, aiming at developing and studying a new mechanism of photocatalyzed atom transfer radical polymerization (ATRP). After a bibliographic study presenting the state-of-the-art in the domain of CRPs under light irradiation (chapter 1), a bis(1,10-phenanthroline) copper (I) complex (Cu(I)) is used as catalyst for the synthesis of well-defined poly(methyl methacrylate)s by ATRP carried out under the irradiation of a low intensity blue LED lamp (chapter 2). The proposed mechanism implies the formation of the excited state Cu(I)* from Cu(I) under irradiation, followed by its oxidative quenching by the brominated compounds, generating the growing active species and the deactivator form of the complex Cu(II). The catalytic cycle is then completed by the addition of triethylamine as a reducing agent enabling the in situ regeneration of the activator form of the complex Cu(I), therefore leading to a faster polymerization. Glycidyl methacrylate is then considered as a comonomer playing simultaneously the role of a reducing agent (chapter 3). Well-defined functional copolymers, with a controlled distribution of epoxide side groups, are thus synthesized. Finally, the photocatalyzed ATRP mechanism is improved by developing a procedure permitting the in situ generation of the activator Cu(I) starting directly from an air-stable Cu(II) complex (chapter 4). The mechanism developed in this way exhibits a good tolerance to the presence of oxygen or inhibitor in the reaction medium. The effects of several parameters (light intensity, ligand concentration and nature of the solvent or counter-ion) are studied, suggesting a photo-induced ligand-exchange as an additional photochemical process implied in the studied photocatalyzed ATRP mechanism.

A presente Tese, elaborada pela integração de artigos científicos publicados ou submetidos em periódicos internacionais, tem por objetivo geral investigar as potencialidades e limitações de resíduos industriais, acadêmicos e agroindustriais na obtenção de catalisadores para degradação de poluentes orgânicos. Foram utilizados resíduos industriais (banhos de galvanização, areias de fundição e petroquímico), acadêmicos (soluções residuais de aula de fotografia contendo prata e solução residual das aulas de química analítica contendo metais) e agro-industriais (casca de arroz, casca de acácia esgotada, pó de fumo) na preparação dos fotocatalisadores suportados. Os sólidos foram caracterizados por um conjunto de técnicas espectroscópicas, volumétricas, microscópicas, eletroquímicas visando descrever os catalisadores do ponto de vista, elementar, estrutural, textural e morfológico, como espectroscopia de emissão de raios X por dispersão de energia (SEM-EDX), espectroscopia de retroespalhamento Rutherford (RBS), espectroscopia de reflectância difusa no ultravioleta (DRS-UV), espectroscopia de espalhamento de raios X em baixo ângulo (SAXS), espectroscopia de fotoelétrons excitados por raios X (XPS), porosimetria de nitrogênio e medidas de potencial zeta (ZP). Os sistemas foram avaliados na fotodegradação de corante (rodamina B), fenol e fármacos sob radiação ultravioleta e visível. Para fins de comparação, titânia comercial P25 (Degussa) foi empregada como catalisador. Além disso, o efeito da reutilização dos catalisadores e atividade fotocatalitica frente a amostras reais foram estudados. O catalisador suportado preparado a partir do resíduo da indústria petroquímica e suportado em sílica apresentou a melhor atividade fotocatalítica na degradação de todas as moléculas testadas, tal como RhB (67 % sob radiação UV e 61 % sob radiação visível), fármaco guaifenesin ( 49 % UV e 45 % visível) e fenol (44 % UV), enquanto que o P25 comercial apresentou 93 % e 14 %, respectivamente, para a radiação ultravioleta e visível. / This thesis, developed by the integration of scientific papers published or submitted in international journals, has the objective to investigate the potential and limitations of industrial waste, academics and agroindustrial to obtain catalysts for degradation of organic pollutants. Industrial waste (galvanic baths, foundry sands and petrochemical), academics (residual solutions of class photograph containing silver and residual solution of analytical chemistry classes containing metals) and agroindustrial (rice husk, exhausted bark acacia, tobacco dust) were used in the preparation of the supported photocatalyst. The solids were characterized by a set of spectroscopic, volumetric, microscopic electrochemical techniques in order to describe elementary structural, textural and morphological properties, such as Scanning electron microscopy with energy dispersive X-ray spectroscopy (SEM-EDX), Rutherford backscattering spectrometry (RBS), diffuse reflectance spectroscopy in the ultraviolet (DRS-UV), small-angle X-ray scattering (SAXS), X-ray Photoelectron Spectroscopy (XPS), nitrogen porosimetry and zeta potential (ZP) measurements. The catalyst activity was evaluated on the dye (RhB), phenol and drugs photodegradation under ultraviolet and visible radiation. For comparative reasons, P25 (Degussa) was also employed as the catalyst. Furthermore, the effect of reuse of catalysts and photocatalytic activity compared to real samples were also evaluated. The silica supported catalyst prepared from petrochemical waste and supported on silica showed the best photocatalytic activity in the degradation of all tested molecules, such as RhB (67% and 61% under UV and visible radiation, respectively), guaifenesin drug (49% UV and 45 % visible radiation) and phenol (44 % UV radiation), while the commercial P25 showed 93 % and 14 %, to ultraviolet and visible radiation, respectively.

É urgente o desenvolvimento de novas tecnologias para o tratamento de água nos dias atuais. Neste contexto, os processos oxidativos avançados (POA) tem sido bem-sucedido no tratamento de contaminantes presentes em efluentes industriais e na rede de esgoto doméstico. Neste trabalho, estudamos um dos POA, a fotocatáliseheterogênea por meio da síntese de fotocatalisadores mistos de nióbio e titânio utilizando-se o método Pechini, com uma temperatura de calcinação de 470 oC. Foram sintetizados os fotocatalisadores PNB000, PNB018, PNB030, PNB070, PNB099 e PNB100, onde os números mostram aporcentagem em mols de pentóxido de nióbio presente em cada um deles. Estes fotocatalisadores foram submetidos a um segundo tratamento térmico a 800oC, durante 6 horas, e obtivemoso PNB000_01, PNB018_01, PNB030_01, PNB070_01 e PNB100_01. A caracterização dos fotocatalisadores foi feita por: análise de espectroscopia de energia dispersiva (EDS); área superficial determinadas por isotermas de adsorção e dessorção de nitrogênio, BET; imagens de microscopiaeletrônica de varredura (MEV); difração de raios-X; análises térmicas (termogravimetria e análise térmica diferencial), determinação de band gap por reflectância difusa. O potencial para serem usados como fotocatalisadores heterogêneos para degradação de compostos orgânicos foi avaliado pela eficiência fotônica de geração de radicais hidroxilas(OH)sob radiação de lâmpada UVA (15 W). A análise de EDS confirmou acomposiçãoem mol de TiO2 e Nb2O5presentes nosfotocatalisadoressintetizados. A área superficial obtida por isotermas (BET) do PNB018 (161,7 m²/g), PNB030 (130,8 m²/g), PNB070 (150,5 m²/g) mostraram-se maiores do que ado TiO2 P25 (52,68 m²/g). As imagens de MEV mostrou que estes fotocatalisadoressão constituídos de partículas manométricas. Outra característica dos óxidos com quantidade intermediária de mols de Nb2O5 (18, 30 e 70%) foi a estrutura amorfa determinada por difração de raios-X. Por sua vez, os óxidos tratados a 800oC apresentaram estruturas cristalinas edifratogramas de raios-X completamente diferentes do TiO2 e do Nb2O5, comprovando-se que são novos materiais.As medidas de energia de band gapmostrou diferenças significativas quando comparamos o TiO2 P25 (Egap 3,22eV) e o PNB000 (Egap 2,90eV). Isso leva a concluir que estes fotocatalisadores sintetizados pelo método Pechini necessitam de uma energia menor para que ocorram as transições eletrônicas. O fotocatalisador PNB070, que apresenta 70% em mols de pentóxido de nióbio, apresentouOH de 0,104 da mesma ordem de grandeza do TiO2 P25 (OH 0,134) e ligeiramente menor do que o OH do Nb2O5.nH2O (OH 0,164). Dessa maneira, supõe-se que o PNB070 tenha o mesmo potencial de eficiência que o TiO2 P25 para fotodegradações. Por sua vez, os fotocatalisadores que passaram por um segundo tratamento térmico a 800 oC mostraram valores de rendimento quântico de produção de radicais hidroxilas bem inferiores aos seus originais. Por exemplo, o PNB070_01 teve OH de 0,003. Esses resultados sugerem que o aumento da cristalinidade pode diminuir a atividade fotocatalítica, ou, que o estado amorfo dos fotocatalisadores deste trabalho favorece o aumento da velocidade de transferência de elétrons e a da fotocatálise. / Nowadays, the development of new technologies for the treatment of water is urgent. In this context, the advanced oxidative processes (AOP) has been successful in the treatment of contaminants foundin industrial effluents and domestic sewage. In this work, we have studied an AOP, the heterogenousphotocatalysis, by means the synthesis of niobium and titanium mixedphotocatalysts, employing calcination temperature of 470 oC.The PNB000, PNB018, PNB030, PNB070, PNB099 and PNB100photocatalysts were synthetized, where the numbers show the percentage in mol of Nb2O5content in each of them. These photocatalytswere submitted to a second heat treatment to 800oC during 6 hours, and PNB000_01, PNB018_01, PNB030_01, PNB070_01 and PNB100_01 were obtained. The characterization of the photocatalysts was made by: analysis of the energy dispersive spectroscopy (EDS); the surface area determined by adsorption and desorption isotherms of nitrogen, BET; images of scanning electron microscopy (SEM); X-ray diffraction; thermal analysis (thermogravimetry and differential thermal analysis), determination of the band gap by diffuse reflectance.Their potential to be used as heterogeneous photocatalystsfor degradation of organic compounds was evaluated by means the determination of the photonic efficiency for hydroxyl radical production (OH)under radiation of UV-A lamp (15 W). The EDS analysis confirmed the composition in mol of TiO2 and Nb2O5 present in the synthesizedphotocatalysts. Surface area obtained by isotherms (BET) of PNB018 (161.7 m ²/g), PNB030 (130.8 m ²/g), PNB070 (150.5 m ²/g) were higher than TiO2 P25 (52.68 m ²/g). SEM images showed that these photocatalysts consist of nanoparticles. Another feature of the oxides with intermediate amount of moles of Nb2O5 (18, 30 and 70%) was the amorphous structure determined by X-ray diffraction. On the other hand, the oxides treated to 800 oC showed crystalline structures and X-ray patternscompletely different from TiO2 and Nb2O5, proving that the synthetized oxides are new materials.The band gap energy measurements showed significant differences when we compare TiO2 P25 (Egap 3.22 eV) and the PNB000 (Egap 2.90 eV). This allow us to conclude that thephotocatalysts synthesized by Pechini method require lower energy in order to have electronic transitions. The PNB070 photocatalyst, which has 70% in mols of niobium pentoxide, showed OHof 0.104 of the same order of magnitude of TiO2 P25 (OH0.134) and slightly smaller than the OH of Nb2O5.nH2O (OH 0.164). For this reason, we can assume that PNB070 has the same potential of the TiO2 P25 for organic compound photodegradation. The photocatalyststhat were submittedthrough a second heat treatment at 800 oC showed quantum efficiency of hydroxyl radical production values well below their original. For instance, PNB070_01 showed OHof 0.003. These results suggest that increased crystallinity can reduce the photocatalytic activity, or the amorphous structures of the photocatalysts of this work improve the electron transfer rates and the photocatalysis.

Submitted by Maria Aparecida (cidazen@gmail.com) on 2017-11-16T12:37:19Z No. of bitstreams: 1 ANTONIO DE JESUS DOS SANTOS FERNANDES JÚNIOR.pdf: 2676930 bytes, checksum: 6ea43214cce79a1ebadd7cae50663205 (MD5) / Made available in DSpace on 2017-11-16T12:37:19Z (GMT). No. of bitstreams: 1 ANTONIO DE JESUS DOS SANTOS FERNANDES JÚNIOR.pdf: 2676930 bytes, checksum: 6ea43214cce79a1ebadd7cae50663205 (MD5) Previous issue date: 2017-09-05 / In this work,a nevel material heterostructured based on the assembly of double layered double hydroxide (LDH) suported in magadiite, was synthesized. For this purpose, layered double hydroxides of MgAl and ZnAl,both in the proportion 2:1 was synthesized by the method of coprecipitation in situ in the presence of magadiite.Diverse physicochemical techniques (DRX,FTIR,DTA,ICP-OES,MEV E TEM ) were employed to caractherize the materials syntehesized with the aim of verifying the existence of interactions in the interface of both components. Results gotten by DRX show plans of reflection typical of magadiite,confirming the formation o HDL in the surface of silicate. Nanocrystalline interactions among the groups of hydroxyl of each component. Metalic Oxide nanoparticles were supported in magadiite employing the thermic decomposition (calcination) of the component HDL present in the hetero-structure MAG/HDL,with the aim of getting catalyst formed by metalic oxides highly dispersed supported in magadiite. Calcined materials and non-calcined were evaluated as photocatalysts, using blue dye of methylene as a standard molecule. Photocatalytic analyses were made with “heterostructure” MAG/HDL and MAG/ODL showed a catalytic activity improved in order to degradate the dye,,where the concentration decreased considerablly in a short interlude of exposition to irradiation of uv light in camparison to the photlysis test.These results were gotten probably thanks to the resulting synergistic effect of textured properties interesting,charactheristics of synthesized heterostructured ,turning them in photocatalytic promising in the degradation of organic compounds. / Neste trabalho, um novo material heteroestruturado baseado na síntese de hidróxidos duplos lamelares suportados em magadiíta, foi sintetizado. Para este fim, hidróxidos duplos lamelares (HDL) de MgAl e ZnAl, ambos nas proporções 2:1, foram sintetizados pelo método de coprecipitação in situ em presença do silicato alcalino lamelar. Diversas técnicas físico-químicas (DRX, FTIR, DTA, ICP-OES, MEV e TEM) foram empregados para caracterizar os materiais sintetizados com o objetivo de verificar a existência a existência de interações na interface dos dois componentes. Resultados obtidos por DRX mostram planos de reflexão típicos de magadiíta, confirmando a formação de HDL na superfície do silicato. Interações nanocristalinas entre as porções foram evidenciadas por estudos de espectroscopia onde ocorrem interações entre os grupos hidroxilas de cada componente. Nanopartículas de óxidos metálicos foram suportados em magadiíta empregando a decomposição térmica (calcinação) do componente HDL presente na heteroestrutura MAG/HDL, com o objetivo de obter-se materiais catalisadores formados por óxidos metálicos altamente dispersos suportados em magadiíta. Os materiais calcinados e não calcinados foram avaliados como fotocatalisadores, usando o corante azul de metileno como molécula modelo. Testes fotocatalíticos realizados com as heteroestruturas MAG/HDL e MAG/ODL mostraram uma atividade catalítica melhorada para a degradação do corante, onde a concentração diminuiu consideravelmente em um curto intervalo de tempo de exposição à irradiação de luz UV em comparação ao teste de fotólise. Estes resultados foram obtidos provavelmente devido ao efeito sinérgico resultante das propriedades texturais interessantes, características das heteroestruturas sintetizadas, tornando-os fotocatalisadores promissores na degradação de compostos orgânincos.

京都大学 / 新制・課程博士 / 博士(人間・環境学) / 甲第23976号 / 人博第1028号 / 新制||人||242(附属図書館) / 2022||人博||1028(吉田南総合図書館) / 京都大学大学院人間・環境学研究科相関環境学専攻 / (主査)教授 吉田 寿雄, 教授 田部 勢津久, 教授 中村 敏浩 / 学位規則第4条第1項該当 / Doctor of Human and Environmental Studies / Kyoto University / DFAM

Magnetic photocatalysts were synthesised by coating a magnetic core with a layer of photoactive titanium dioxide. This magnetic photocatalyst is for use in slurry-type reactors in which the catalyst can be easily recovered by the application of an external magnetic field. The first attempt at producing this magnetic photocatalyst involved the direct deposition of titanium dioxide onto the surface of magnetic iron oxide particles. The photoactivity of these Fe3O4/TiO2 was lower than that of single-phase TiO2 and was found to decrease with an increase in the heat treatment. These observations were explained in terms of an unfavourable heterojunction between the titanium dioxide and the iron oxide core. Fe ion diffusion from the iron oxide core into the titanium dioxide matrix upon heat treatment, leading to a highly doped TiO2 lattice, was also contributing to the observed low activities of these samples. These Fe3O4/TiO2 particles were found to be unstable, with photodissolution of the iron oxide phase being encountered. This photodissolution was dependent on the heat treatment applied, the greater the extent of the heat treatment, the lower the incidence of photodissolution. This was explained in terms of the stability of the iron oxide phases present, as well as the lower photoactivity of the titanium dioxide matrix. In fact, the observed photodissolution was found to be induced-photodissolution. That is, the photogenerated electrons in the titanium dioxide phase were being injected into the lower lying conduction band of the iron oxide core, leading to its reduction and then dissolution. Thus, the approach of directly depositing TiO2 onto the surface of a magnetic iron oxide core proved ineffective in producing a stable magnetic photocatalyst. The introduction of an intermediate passive SiO2 layer between the titanium dioxide phase and the iron oxide phase inhibited the direct electrical contact and hence prevented the photodissolution of the iron oxide phase. Improvements in the photoactivity were seen to be due to the inhibition of both the electronic and chemical interactions between the iron oxide and titanium dioxide phases. Preliminary optimisation experiments revealed that a thin SiO2 layer is sufficient for inhibiting the photodissolution. The thickness of the TiO2 coating was found not to have a significant effect on the photocatalytic performance of the coated particles. Finally, heat treating for 20 minutes at 450??C was sufficient for converting the titanium dioxide into a photoactive phase, longer heating times had no beneficial effect on the photoactivity.

This study applied sputtering technology to prepare composite film photocatalyst TiO2/ITO for investigating the decomposition efficiency of acetone using composite TiO2/ITO made by single- and multi-layer processes. The influences of operating parameters, including sputtering operating parameters and photocatalytic operating parameters, on the decomposition efficiency of acetone were further investigated. Operating parameters investigated for the sputtering process included oxygen to argon ratio (O2/Ar), temperature, substrate, sputtering dutation, and sputtering layers, while operating parameters investigated for the photocatalytic decomposition of acetone included light wavelength, H2O concentration, O2 concentration, initial acetone concentration, and the type of photocatalysts. In the experiments, acetone was degraded by the composite film photocatalyst TiO2/ITO in a self-designed batch photocatalytic reactor. Operating parameters included light wavelength (350~400 nm, 435~500 nm, 506~600 nm), the type of photocatalysts (single-layer film photocatalyst TiO2/ITO with the thickness of 355.3, 396.6, 437.5, 487.5, and 637.5 nm; double- and triple-layer TiO2/ITO), H2O concentration (0, 50, 100, 200, and 300 ppm). The incident light with different wavelength irradiated with three 15-W lamps of near UV light or LED lamps of blue and green lights placed on the top of the photocatalytic reactor. Acetone was injected into the reactor by using a gasket syringe and vaporized for further photocatalytic degradation on the film photocatalyst TiO2/ITO placed at the bottom of the reactor. Air samples were taken to analyze acetone concentration with a GC/FID. The composite film photocatalyst TiO2/ITO was mainly composed of anatase with a few rutile. The thicknesses of the single- and IV double-layer film photocatalyst with the thickness of 473.5 nm and 506.0 nm, respectively. Experimental results indicated that the highest decomposition efficiency of acetone was obtained by using TiO2/ITO, followed by TiO2/ground glass and TiO2/glass. The highest decomposition efficiency of acetone was observed by using TiO2/ITO at 50¢XC, 20% O2, and 100 ppm H2O. In the kinetic model, the acetone decomposition of single-layer TiO2/ITO was zero-order reaction. The acetone decomposition of double-layer TiO2/ITO in high initial acetone concentration was zero-order reaction, while that in low initial acetone concentration was first-order reaction. Thus, the decomposition of acetone exerted by TiO2 film photocatalyst can be enhanced efficiently by ITO. Under the incidence of blue light, the reaction rate of acetone decomposition were 2.353¡Ñ10-5 and 3.478¡Ñ10-5 £gmole/cm2-s for using single- and double-layer TiO2/ITO, respectively. Finally, a bimolecular Langmuir-Hinshelwood (L-H) kinetic model was applied to simulate the influences of initial acetone concentration, temperature, and relative humidity on the promotion and inhibition for the photocatalytic degradation of acetone. This study revealed that the L-H kinetic model could successfully simulate the photocatalytic reaction rate of acetone.

The study combined photoelectrocatalytic technology (PEC) with electrical glassfiber filter (EGF) to decompose volatile organic compounds (VOCs). External electrical voltage was applied to retard the recombination of electron-electron hole pairs and increase the surface temperature of the photocatalysts coated on the electrical glassfiber filter, which could further decompose VOCs more effectively via photoelectrocatalytic technology. Acetone was selected as the gasous pollutant for this particular study. A commercial TiO2 photocatalyst (AG-160) was coated on GFF via impregnation to decompose acetone in a batch PEC reactor. Operation parameters investigated in this study included acetone concentration (50~400 ppm), electrical voltage (0~6,500V), water content (0~20,000 ppm), reaction temperature (40¢J~80¢J).The incident UV light of 365 nm wavelength was irradiated by three 15-wat low pressure mercury lamps (£f=365 nm) placing above the batch PEC reactor. The TiO2-coated EGF was placed at the center of the batch PEC reactor. Acetone was injected into the reactor by a gasket syringe to conduct the PEC decomposition test. Acetone was analyzed quantitatively by a gas chromatography with a flame ionization detector (GC/FID). Finally, a Langmuir-Hinshelwood kinetic (L-H) model was proposed to simulate the PEC reaction rate of acetone. Experimental results showed that the size range of the self-produced nano-sized photocatalyst prepared by sol-gel was 35~50 nm. Three duplicate tests of PC and PEC degradation of acetone indicated that TiO2 was not deactivated during the PC and PCE reactions, hence TiO2 can be reused in the experiments. Results obtained from the PC and PEC degradation experiments indicated that the PEC reaction rate was higher than the PC reaction rate.The PEC reaction rate increased with applied electrical voltage, and the highest decomposition efficiency occurred at 6,500 V. Electrical field generated by the differences of electrical voltage can effectively enhance the oxidation capability of TiO2 since electron (e-) can be conducted to retard the recombination of electron and electron hole pairs. Both PC and PEC technologies could be used to decompose acetone. Among them, PEC had highter decomposition efficiency of acetone than PC up to 34%. Rsults obtained from the operation parameter tests reaveled that raising electrical voltage could enhance the decomposition efficiency of acetone only for electrical voltages above 2,000 V. However, the decomposition efficiency of acetone tended to level off as electrical voltage became higher. Zero-order reaction rate of the PEC reaction was observed for initial acetone concentration of 100~400 ppm, while the PEC reaction decreased gradually for initial acetone concentration reaction below 100 ppm. It revealed that the PEC reaction was pseudo ozero-order for initial acetone concentration of 100~400 ppm, and pseudo first-order reaction for acetone concentration below 100 ppm. Additionally, the PC reaction rate increased with temperature at 45-80¢J. However the PEC reaction rate increased with temperature at 45-60¢J, and decreased with temperature at 60-80¢J. An adsorptive competition between acetone and water molecules at the active sites over TiO2 surface caused either promotion or inhibition of TiO2 decomposition depending on moisture content . For the PC and PEC reactions, the optimum operating condition of water vapor concentration was 10,000 ppm, but inhibition occurred when the water vapor concentration increased up to 20,000 ppm. Finally, the Langmuir-Hinshelwood kinetic model was applied to investiage the influences of reaction temperature, initial concentration of acetone, and water content on the photoelectrocatalytic reaction rate of acetone. Model simulation results showed that photoelectrocatalytic reaction rate constant of acetone(kLH) and adsorptive equilibrium constant(KA) increased with electrical voltage and acetone initial concentration. This study sevealed that experimental and simulated results were in good agreement. Thus, PEC reaction rate of acetone on the surface of TiO2 can be also succesfully simulated by the L-H kinetic model.