The effect of titanium dioxide (TiO2) on the properties of color conversion glasses was examined for glasses based on BaO-ZnO-B2O3-SiO2. One glass sample, containing 25 mol% of each component, was used as a reference; the other three glass samples contained 1, 3, and 5 mol% TiO2, respectively. The four color conversion glass samples were prepared by sintering a mixture of glass frits and a YAG:Ce+ phosphor. The characteristics of the color conversion glass samples, such as luminous efficacy, luminance, CIE (Commission International de I'Eclairage) chromaticity, CCT (Correlated Color Temperature), and CRI (Color Rendering Index) were analyzed according to the PL spectrum. The refractive index of the glass samples was found to increase with the titanium dioxide content. In conclusion, luminous efficacy of color conversion glasses increased as the content of TiO2 was raised in the glass matrix.

To synthesize a high-performance photocatalyst, N doped TiO2 nanotubes deposited with Ag nanoparticles were synthesized, and surface characteristics, electrochemical behaviors, and photocatalytic activity were investigated. The TiO2 nanotubular photocatalyst was fabricated by anodization; the Ag nanoparticles on the TiO2 nanotubes were synthesized by a reduction reaction in AgNO3 solution under UV irradiation. The XPS results of the N doped TiO2 nanotubes showed that the incorporated nitrogen ions were located in interstitial sites of the TiO2 crystal structure. The N doped titania nanotubes exhibited a high dye degradation rate, which is effectively attributable to the increase of visible light absorption due to interstitial nitrogen ions in the crystalline TiO2 structure. Moreover, the precipitated Ag particles on the titania nanotubes led to a decrease in the rate of electron-hole recombination; the photocurrent of this electrode was higher than that of the pure titania electrode. From electrochemical and dye degradation results, the photocurrent and photocatalytic efficiency were found to have been significantly affected by N doping and the deposition of Ag particles.

본 연구에서는 정제되지 않은 ZnO 및 TiO₂나노입자를 M4배지에 노출시켜 두 나노입자가 어느 정도 크기의 응집체로 변화되는지를 살펴보고 또한 두 나노입자가 수생태계 생물종인 Daphnia magna에 어떠한 영향을 초래하는지 유영저해 및 폐사율을 통해 살펴보았다. ZnO 및 TiO₂나노입자의 분말상태 크기는 각각 20 nm와 40 nm였지만, M4배지에서는 1333 nm와 1628 nm로 약 40~70배의 크기로 응집되었다. 유영저해의 경우 ZnO와 TiO₂나노입자 모두 시간 및 농도가 높아질수록 D.magna가 유영하는데 영향을 미친 것으로 나타났으며, 특히 ZnO나노입자가 TiO₂나노입자에 비해 더 큰 영향을 미치는 것으로 나타났다. 폐사율의 경우 ZnO나노입자에서는 시간 및 농도가 높아질수록 폐사되는 비율이 높았으며, TiO₂나노입자에서는 72시간이 경과된 시점의 10 ppm 이상의 농도에서 폐사하는 것으로 관찰되었다. 이는 나노입자가 해양에 유입됨으로 인해 원래의 크기에 비해 응집되어 증가되어진다는 것을 알 수 있으며, 또한 그 응집체로 인해 수생태계 생물에 영향을 주는 것으로 나타났다.

PURPOSES: In areas of high traffic volume, such as expressway across large cities, the amount of nitrogen oxides (NOx) emitted into the atmosphere as air pollution can be significant since NOx gases are the major cause of smog and acid rain. Recently, the importance of NOx removal has arisen in the world. Titanium dioxide (TiO2), that is one of photocatalytic reaction material, is very efficient for removing NOx. The NOx removing mechanism of TiO2 is the reaction of solar photocatalysis. Therefore, TiO2 in road structure concrete need to be contacted with ultraviolet rays (UV) to be activated. In general, TiO2 concretes are produced by replacement of TiO2 as a part of concrete binder. However, considerable portion of TiO2 in concrete cannot contact with the pollutant in the air and UV. Therefore, TiO2 penetration method using the surface penetration agents is attempted as an alternative in order to locate TiO2 to the surface of concrete structure. METHODS: This study aimed to evaluate the NOx removal efficiency of photocatalytic concrete due to various TiO2 application method such as mix with TiO2, surface spray(TiO2 penetration method) on hardened concrete and fresh concrete using surface penetration agents. The NOx removal efficiency of TiO2 concrete was confirmed by NOx Analyzing System based on the specification of ISO 22197-1. RESULTS: The NOx removal efficiency of mix with TiO2 increased from 11 to 25% with increasing of replacement ratio from 3 to 7%. In case of surface spray on hardened concrete, the NOx removal efficiency was about 50% due to application amount of TiO2 with surface penetration agents as 300, 500 and 700g/m2. The NOx removal efficiency of surface spray on fresh concrete due to all experimental conditions, on the other hand, which was very low within 10%. CONCLUSIONS: It was known that the TiO2 penetration method as surface spray on hardened concrete was a good alternative in order to remove the NOx gases for concrete road structures.

본 연구는 염료감응형 태양전지를 이용하여 시간에 따른 일사량과 그에 따른 전력량의 분석을 통해 계절적 변화에 따른 온실 적용 염료감응형 태양전지의 효율에 관한 기초 자료 수집 및 분석을 목표로 하였다. 경상대 학교 소재 온실 근처(위도 35o 9' 9.20" N, 경도 128o 5' 44.90" E, 고도 52m)에 태양전지 어레이를 설치, 2012 년 8월, 10월, 11월, 2013년 2월 약 네 달 동안 태양전 지가 받는 일사량과 그에 따른 전력량을 측정 및 비교, 분석하였다. 10월의 태양전지 패널 면적에 따른 일사량이 약 1,013.03MJ, 발생된 전력량은 약 4.87kWh로 네 달 중 가장 높게 측정되었고, 11월의 패널 면적에 따른 일사량이 약 755.25MJ, 발생 전력량은 약 3.34kWh로 가장 낮게 측정되었다. 염료감응형 태양전지의 평균 효율의 경 우 8월 한 달간, 약 3.12%로 측정되었고, 10월 2.60%, 11월 2.39%, 2월 2.23%로 각각 측정되었다. 본 연구를 통해, 향후 염료감응형 태양전지의 온실 등 농업분야 적 용 시 기초자료로 활용 할 수 있을 것으로 기대된다.

We synthesized Fe-doped TiO2/α-Fe2O3 core-shell nanowires(NWs) by means of a co-electrospinning method anddemonstrated their magnetic properties. To investigate the structural, morphological, chemical, and magnetic properties of thesamples, X-ray diffraction, scanning electron microscopy, transmission electron microscopy, and X-ray photoelectronspectroscopy were used, as was a vibrating sample magnetometer. The morphology of the nanostructures obtained aftercalcination at 500oC exhibited core/shell NWs consisting of TiO2 in the core region and α-Fe2O3 in the shell region. In addition,the XPS results confirmed the formation of Fe-doped TiO2 by the doping effect of Fe3+ ions into the TiO2 lattice, which canaffect the ferromagnetic properties in the core region. For comparison, pure α-Fe2O3 NWs were also fabricated using anelectrospinning method. With regard to the magnetic properties, the Fe-doped TiO2/α-Fe2O3 core-shell NWs exhibited improvedsaturation magnetization(Ms) of approximately ~2.96emu/g, which is approximately 6.1 times larger than that of pure α-Fe2O3NWs. The performance enhancement can be explained by three main mechanisms: the doping effect of Fe ions into the TiO2lattice, the size effect of the Fe2O3 nanoparticles, and the structural effect of the core-shell nanostructures.

Pt has been widely used as catalyst for fuel cell and exhausted gas clean systems due to its high catalytic activity.Recently, there have been researches on fabricating composite materials of Pt as a method of reducing the amount of Pt due toits high price. One of the approaches for saving Pt used as catalyst is a core shell structure consisting of Pt layer on the core ofthe non-noble metal. In this study, the synthesis of Pt shell was conducted on the surface of TiO2 particle, a non-noble material,by applying ultraviolet (UV) irradiation. Anatase TiO2 particles with the average size of 20~30 nm were immersed in the eth-anol dissolved with Pt precursor of H2PtCl6·6H2O and exposed to UV irradiation with the wavelength of 365 nm. It was con-firmed that Pt nano-particles were formed on the surface of TiO2 particles by photochemical reduction of Pt ion from the solution.The morphology of the synthesized Pt@TiO2 nano-composite was examined by TEM (Transmission Electron Microscopy).

In the present work, WO3 and WO3-TiO2 were prepared by the chemical deposition method. Structural variations, surface state and elemental compositions were investigated for preparation of WO3-TiO2 sonocatalyst. X-ray diffraction (XRD), scanning electron microscopy (SEM), energy dispersive X-ray (EDX) and transmission electron microscopy (TEM) were employed for characterization of these new photocatalysts. A rhodamine B (Rh.B) solution under ultrasonic irradiation was used to determine the catalytic activity. Excellent catalytic degradation of an Rh.B solution was observed using the WO3-TiO2 composites under ultrasonic irradiation. Sonocatalytic degradation is a novel technology of treating wastewater. During the ultrasonic treatment of aqueous solutions sonoluminescence, cavitaties and "hot spot" occurred, leading to the dissociation of water molecules. In case of a WO3 coupled system, a semiconductor coupled with two components has a beneficial role in improving charge separation and enhancing TiO2 response to ultrasonic radiations. In case of the addition of WO3 as new matter, the excited electrons from the WO3 particles are quickly transferred to TiO2 particle, as the conduction band of WO3 is 0.74 eV which is -0.5 eV more than that of TiO2. This transfer of charge should enhance the oxidation of the adsorbed organic substrate. The result shows that the photocatalytic performance of TiO2 nanoparticles was improved by loading WO3.

Fe4[Fe(CN)6]3 coated on a mica or TiO2/mica surface as infrared reflective blue pigment was prepared by a hydrothermal method. Fe4[Fe(CN)6]3, used as coloring agent, was uniformly coated on mica or TiO2/mica under the optimized condition of a 1.2 : 1 weight ratio between iron(III) chloride hexahydrate and potassium ferrocyanidetrihydrate at the initial pH level of 4.5 at 70˚C. The infrared (IR)-reflective pigments were characterized by SEM, Zeta-potenial, FT-IR, and UV-VIS NIR spectrophotometry. Especially the CIE color coordinate and total solar reflectance(TSR) properties of the pigments were investigated in relation to variation of the coating and coated substrate thicknesses. Isolation-heat paint was prepared with 20 wt% blue pigments fully dispersed in acryl-urethane resin and several additives to coat the film uniformly. The films were also measured with CIE color coordinate, TSR, and the surface temperature was recorded by an isolation-heat measuring system. The pigments and films of Fe4[Fe(CN)6]3 coated on mica and TiO2/mica showed high TSR values compared with the TSR value of Fe4[Fe(CN)6]3 itself. According to the increase of TSR value, the property of isolation-heat is effective. To realize the optimal blue color, we applied the the pigment to TiO2 coated mica(TM(b)) which has blueish interference color. The pigment of Fe4[Fe(CN)6]3 coated on TM(b) shows a strong blue color compared with that of Fe4[Fe(CN)6]3 coated on TiO2/Mmca(TM(w)), which has a whitish interference color.

The most general photocatalyst, TiO2 and WO3, are acknowledged to be ineffective in range of visible light. Therefore, many efforts have been directed at improving their activity such as: band-gap narrowing with non-metal element doping and making composites with high specific surface area to effectively separate electrons and holes. In this paper, the method was introduced to prepare a photo-active catalyst to visible irradiation by making a mixture with TiO2 and WO3. In the TiO2-WO3 composite, WO3 absorbs visible light creating excited electrons and holes while some of the excited electrons move to TiO2 and the holes remain in WO3. This charge separation reduces electron-hole recombination resulting in an enhancement of photocatalytic activity. Added Ag plays the role of electron acceptor, retarding the recombination rate of excited electrons and holes. In making a mixture of TiO2-WO3 composite, the mixing route affects the photocatalytic activity. The planetary ball-mill method is more effective than magnetic stirring route, owing to a more effective dispersion of aggregated powders. The volume ratio of TiO2(4) and WO3(6) shows the most effective photocatalytic activity in the range of visible light in the view point of effective separation of electrons and holes.

본 시험은 괘대재배를 한 ‘풍수’, ‘황금배’, ‘신고’, 그리고 ‘감천배’의 관행구와 무대재배를 한 과실에 TiO2나 Kaolin를 엽면처리 하였을 때 과실품질과 흑성병에 미치는 영향을 조사하고자 수행되었다. 1. 관행재배구는 TiO2나 Kaolin 보다 평균과중은 증가하였지만, 수량이 현저하게 감소하여 총 과실생산량은 감소되었다.2. 관행재배구에서의 ‘풍수’와 ‘감천배’의 당도는 TiO2나Kaolin 처리구 보다 높았다.3. ‘황금배’와 ‘감천배’의 과실 경도는 TiO2 처리시 가장 높았으며 Kaolin처리시도 다소 증가시켰다. ‘풍수’와 ‘신고’는 처리 간에 차이가 없었다.4. 과피색은 관행재배구에서 가장 밝은 색도를 보였다.5. TiO2와 Kaolin 처리는 품종에 상관없이 총 폴리페놀 함량을 증가시켰다.6. 엽의 흑성병 발생 억제율은 관행재배구가 ‘풍수’, ‘황금배’,‘신고’에서 낮게 나타났으며 ‘감천배’는 TiO2 처리로 100% 억제되었다.

This study shows an air-purification test by the UV lamp on which TiO2 catalyst is deposited with glass fiber in the reactor chamber. This test was based on the fundamental data of air-purifier as assessing a removing ability on various contaminants such as CH3COOH, NH3, NO and SO2 as variation of the TiO2 coating, the wave of UV lamp, and the additive CaO. As a result, the highest decomposing removal ratio was shown when 5-times coated glass fiber was used. It can be due to the recombination reaction of electrons and electron-hole in the loaded CaO. Thus, the decomposing removal ratio increased as the recombination ratio decreased. In addition, it was confirmed that the decomposing removal ratio lowered when CaO was considerably deposited because it hided the lamp of OH-1 radical.

Electrochemical surface treatment is commonly used to form a thin, rough, and porous oxidation layer on the surface of titanium. The purpose of this study was to investigate the formation of nanotubular titanium oxide arrays during short anodization processing. The specimen used in this study was 99.9% pure cp-Ti (ASTM Grade II) in the form of a disc with diameter of 15 mm and a thickness of 1 mm. A DC power supplier was used with the anodizing apparatus, and the titanium specimen and the platinum plate (3mm×4mm×0.1mm) were connected to an anode and cathode, respectively. The progressive formation of TiO2 nanotubes was observed with FE-SEM (Field Emission Scanning Electron Microscopy). Highly ordered TiO2 nanotubes were formed at a potential of 20 V in a solution of 1M H3PO4 + 1.5 wt.% HF for 10 minutes, corresponding with steady state processing. The diameters and the closed ends of TiO2 nanotubes measured at a value of 50 cumulative percent were 100 nm and 120 nm, respectively. The TiO2 nanotubes had lengths of 500 nm. As the anodization processing reached 10 minutes, the frequency distribution for the diameters and the closed ends of the TiO2 nanotubes was gradually reduced. Short anodization processing for TiO2 nanotubes of within 10 minutes was established.

Excellent electron transport properties with enhanced light scattering ability for light harvesting have made well-ordered one dimensional TiO2 nanotube(TNT) arrays an alternative candidate over TiO2 nanoparticles in the area of solar energy conversion applications. The principal drawback of TNT arrays being activated only by UV light has been addressed by coupling the TNT with secondary materials which are visible light-triggered. As well as extending the absorption region of sunlight, the introduction of these foreign components is also found to influence the charge separation and electron lifetime of TNT. In this study, a novel method to fabricate the TNT-based composite photoelectrodes employing visible responsive CuInS2 (CIS) nanoparticles is presented. The developed method is a square wave pulse-assisted electrochemical deposition approach to wrap the inner and outer walls of a TNT array with CIS nanoparticles. Instead of coating as a dense compact layer of CIS by a conventional non-pulsed-electrochemical deposition method, the nanoparticles pack relatively loosely to form a rough surface which increases the surface area of the composite and results in a higher degree of light scattering within the tubular channels and hence a greater chance of absorption. The excellence coverage of CIS on the tubular TiO2 allows the construction of an effective heterojunction that exhibits enhanced photoelectrochemical performance.

수중 이 취미를 유발시키는 대표적인 미량오염물질인 2-methylisoborneal (MIB)과 geosmin(지오스민)의 배제율을 소수성 polyethersulfone (PES) 나노분리막(분획분자량 : 400 Da)을 적용하여 다양한 용액조성에서 관찰하였다. 실험결과 적용된 모든 조건에서 지오스민이 2-MIB보다 다소 높은 배제율을 나타내었다. 용액의 pH 효과를 관찰한 결과 pH가 증가할수록 2-MIB와 지오스민 양쪽 모두 배제율이 증가하는 경향을 나타내었다. 한편, 수중 자연유기물질의 존재는 두 미량유기물질의 배제율을 크게 증가시켰으며 이와 같은 현상은 높은 pH일수록 더욱 뚜렷하게 나타났다. 소수성 분리막을 친수성 TiO2 입자로 표면코팅 시킨 후 배제율을 관찰한 결과 분리막의 표면을 친수화한 후 소수성인 2-MIB와 지오스민의 배제율은 증가하는 경향을 나타내었다. 따라서 소수성 상호작용은 미량유기물질 나노여과 배제율의 중요한 기작 중 하나임을 확인할 수 있었다.

가시광선에 감응하는 광촉매를 제조하기 위하여 TiO2에 질소(N)를 도핑하여 N-TiO2를 제조하였다. 제조한 광촉매의 결정성, 입자 형상 및 도핑 상태는 XRD, FE-SEM 및 XPS를 이용하여 조사하였다. 제조한 광촉매의 활성 평가는 메틸렌블루의 광분해로 조사하였다. 제조한 광촉매는 anatase type이었으며, pH가 높을수록 결정화도가 향상되었다. 제조한 광촉매의 입자 크기는 pH 2.0에서 5.42 nm, pH 4.7에서 5.99 nm, pH 9.0에서 7.58 nm로, 입자 크기는 pH가 증가 할수록 약간씩 증가하였다. 광촉매의 활성은 결정화도에 비례하였다. TiO2에 N를 도핑하여 제조한 N-TiO2가 가시광선 하에서도 활성을 나타냈다. TiO2에 도핑한 N는 격자 속에 존재하는 것이 아니라 표면에 존재하였다.

작은 고체 분체들은 피커링 유화 체계에서 안정화제로 작용하는 것은 이미 알려진 사실이다. 이 연구에서 우리는 알킬실란 처리 TiO2와 n-헥실알코올, 수계로 안정한 피커링 에멀젼을 제조하였다. TiO2 입자에 의해 안정화된 피커링 에멀젼을 제조하기 위한 최적의 조건은 TiO2 입자의 양과 수상/유상의 비에 의해 결정된다. 피커링 에멀젼의 형태는 물과 n-헥실알코올에 대한 입자들의 젖음성에 의존된다. 피커링 에멀젼은 TiO2가 5.00 wt%, 오일과 수상의 비가 3 : 7인 경우에 가장 안정하였다. 피커링 에멀젼을 형판으로 하여 무기 전조체를 졸-겔 공정에 의해 다공성 분체들이 합성되었다. 합성된 다공성 분체들은 광학 현미경, SEM, BET, XRD 및 EDS에 의해 확인되었다.

본 연구에서는 TiO2 입자를 얻을 수 있는 침전법을 이용하여 TiO2 입자를 제조하였다. TiO2 입자 제조시 사용되는 알콜 용매의 종류와 온도 변화 등의 매개변수가 TiO2 입자의 결정 구조, 입자의 크기 및 형태에 미치는 영향을 조사하였다. TiO2 입자제조시 용매로 사용한 알콜 종류인 methyl alcohol, iso-propylalcohol, 그리고 tert-butylalcohol를 scanning electron microscope(SEM) 분석한 결과 iso-propylalcohol이 가장 좋은 결과를 가져왔다. 그리고 온도 변화를 열분석법을 사용한 결과 200℃에서 500℃까지는 아나타제 구조를 유지하였으나, 800℃에서는 루틸 구조로 전환되었다.

To compare the photocatalytic performances of titania for purification of waste water according to applied voltages and doping, TiO2 films were prepared in a 1.0 M H2SO4 solution containing NH4F at different anodic voltages. Chemical bonding states of F-N-codoped TiO2 were analyzed using surface X-ray photoelectron spectroscopy (XPS). The photocatalytic activity of the co-doped TiO2 films was analyzed by the degradation of aniline blue solution. Nanotubes were formed with thicknesses of 200-300 nm for the films anodized at 30 V, but porous morphology was generated with pores of 1-2 μm for the TiO2 anodized at 180 V. The phenomenon of spark discharge was initiated at about 98 V due to the breakdown of the oxide films in both solutions. XPS analysis revealed the spectra of F1s at 684.3 eV and N1s at 399.8 eV for the TiO2 anodized in the H2SO4-NH4F solution at 180 V, suggesting the incorporation of F and N species during anodization. Dye removal rates for the pure TiO2 anodized at 30 V and 180 V were found to be 14.0% and 38.9%, respectively, in the photocatalytic degradation test of the aniline blue solution for 200 min irradiation; the rates for the F-N-codoped TiO2 anodized at 30 V and 180 V were found to be 21.2% and 65.6%, respectively. From the results of diffuse reflectance absorption spectroscopy (DRS), it was found that the absorption edge of the F-N-codoped TiO2 films shifted toward the visible light region up to 412 nm, indicating that the photocatalytic activity of TiO2 is improved by appropriate doping of F and N by the addition of NH4F.