• 한국세라믹학회지
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• 제44권3호
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• pp.137-141
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• 2007

$La_{2}O_{3}-TiO_{2}-SiO_{2}$ glass, a type that could not obtained so far by the conventional melting method, was prepared successfully using a sol gel process. Glass derived with the sol-gel process has compositions of $5La_{2}O_{3}-5TiO_{2}-90SiO_{2},\;5La_{2}O_{3}-10TiO_{2}-85SiO_{2}$, and $5La_{2}O_{3}-20TiO_{2}75SiO_{2}$. The UV-visible absorption edge of all glass compositions was below 400 nm. The measured density is in the range of 2.55-2.89, and was nearly identical to the calculated density and the refractive index of the glasses derived from the sol-gel ranges from 1.545 to 1.645. The molar additive coefficient of $TiO_{2}$ measured in this ternary system is lower than the calculated value, while the value of $La_{2}O_{3}$ is higher.

• 한국환경과학회지
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• 제13권1호
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• pp.37-40
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• 2004

In this study, the decomposition of gas-phase TCE, Benzene and Toluene, in air streams by direct UV Photolysis and UV/TiO$_2$ process was studied. For direct UV Photolysis, by regressing with computer calculation to the experimental results the value of reaction rate constant k of TCE, Toluene and Benzene in this work were determined to be 0.00392s$\^$-l/, 0.00230s$\^$-1/ and 0.00126s$\^$-1/, respectively. And the adsorption constant K of TCE, Toluene and Benzene in this work were determined to be 0.0519 mol$\^$-l/ ,0.0313mo1$\^$-1/ and 0.0084mo1$\^$-1/, respectively. For UV/TiO$_2$ system by regressing with computer calculation to the experimental results the value of reaction rate constant k of TCE, Toluene, and Benzene in this work were determined to be 5.74g/$\ell$$.$min, 3.85g/$\ell$$.$min, and 1.18g/$\ell$$.$min, respectively. And the catalyst adsorption constant K of TCE, Toluene, and Benzene in this work were determined to be 0.0005㎥/mg, 0.0043㎥/mg and 0.0048㎥/mg, respectively.

• Environmental Engineering Research
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• 제13권4호
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• pp.171-176
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• 2008

Studies on visible-light-driven photocatalysis of air pollutants at indoor air quality (IAQ) levels have been limited. Current study investigated visible-light derived photocatalysis with N-doped and S-doped titanium dioxide ($TiO_2$) for the control of benzene at indoor levels. Two preparation processes were employed for each of the two types of photocatalyst: urea-Degussa P-25 $TiO_2$ and titania-colloid methods for the N-doped $TiO_2$; and titanium isopropoxid- and tetraisopropoxide-thiourea methods for the S-doped $TiO_2$. Furthermore, two coating methods (EDTA- and acetylacetone-dissolving methods) were tested for both the N-doped and S-doped $TiO_2$. The two coating methods exhibited different photocatalytic degradation efficiency for the N-doped photocatalysts, whereas they did not exhibit any difference for the S-doped photocatalysts. In addition, the two doping processes showed different photocatalytic degradation efficiency for both the S-doped and N-doped photocatalysts. For both the N-doped and S-doped $TiO_2$, the photocatalytic oxidation (PCO) efficiency increased as the hydraulic diameter (HD) decreased. The degradation efficiency determined via a PCO system with visible-light induced $TiO_2$ was lower than that with UV-light induced unmodified $TiO_2$, which was obtained from previous studies. Nevertheless, it is noteworthy that for the photocatalytic annular reactor with the HD of 0.5 cm, PCO efficiency increased up to 52% for the N-doped $TiO_2$ and 60% for the S-doped $TiO_2$. Consequently, when combined with the advantage of visible light use over UV light use, it is suggested that with appropriate HD conditions, the visible-light-assisted photocatalytic systems can also become an important tool for improving IAQ.

• 대한화장품학회지
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• 제23권3호
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• pp.134-146
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• 1997

Consumers have recently preferred to purchase extensive UV intercepting products, which are waterproof and free from side effects on skin. Testing Cytoroxicity in SR method, cell survivial ratio of UV-B interceptors decreased above 0.08W/V%, and so did that of UV-A interceptors above 0.06W/V%. Also, Patch-test of inorganic UV interceptors resulted in no skin irritation even below 10.0 and 11.25. UV interceptors in the sunlight showed yellowish discoloration in 5 to 14 days. In absorption curves, UV-B was most suitable for Octyl methoxycinnamate and UV-A for Butyl methoxy dibenzoylmethane. Fro this reason, Nylonpoly UVA/UVB the material of OMC and BMDM coated with Nylon & polyethylene, was used as the organic UV interceptor. And zinc oxide and titanium dioxide was used as inorganic UV ibterceptors. The appropriate mixture ratio of ZnO and TiO2 was 6 to 4.6% of ZnO, 4% of TiO2 and 5% of Nylonpoly UVA/UVB were all combined with our sunscreen cream. The SPF value of in-vivo applied to a guinea pig was 34.9 and that of in-vivo was 38.5. Cyclomerhicone and dimerthicone were used in water-in-Silicone system. Ceryl diverhicone and sorbitan sesquioleate were used as emulsifiers and MgSO4, 7H2O, Mg-stearate/Mg-Al-stearate copolymer as emulsification stabilizers. In practical application, each SPF duration of O/W type and W/S type containing sunscreen cream of the same content showed that W/S type of sunscreen cream was 5 times as durable as the other. This product is fit for using in swimming, climbing or skiing. This research is to minimize skin trouble used by UV interceptors and to make one with proper softness, skin safety and UV intercepting efficiency.

• Bulletin of the Korean Chemical Society
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• 제33권7호
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• pp.2133-2139
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• 2012

A new system using $TiO_2$ (nano-sized, band-gap 3.14 eV)-impregnated spherical ZnS (micro-sized, band-gap 2.73 eV) nano/micro-composites (Ti 0.001, 0.005, 0.01, and 0.05 mol %/ZnS) was developed to enhance the production of hydrogen from methanol/water splitting. The ZnS particles in a spherical morphology with a diameter of about 2-4 mm which can absorb around 455 nm were prepared by hydrothermal method. This material was used as a photocatalyst with loading by nano-sized $TiO_2$ (20-30 nm) for hydrogen production. The evolution of $H_2$ from methanol/water (1:1) photo splitting over the $TiO_2$/ZnS composite in the liquid system was enhanced, compared with that over pure $TiO_2$ and ZnS. In particular, 1.2 mmol of $H_2$ gas was produced after 12 h when 0.005 mol % $TiO_2$/ZnS nano/micro-composite was used. On the basis of cyclic voltammeter (CV) and UV-visible spectrums results, the high photoactivity was attributed to the larger band gap and the lower LUMO in the $TiO_2$/ZnS composite, due to the decreased recombination between the excited electrons and holes.

• 공업화학
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• 제18권2호
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• pp.148-154
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• 2007

본 연구는 이산화티탄 광촉매 반응에 의한 축산폐수 처리에 대하여 연구하였다. 이를 위하여 첨가제의 몰비($(C_2H_5)_2NH_2/Ti(OC_3H_7)_4$)를 1, R 비($H_2O\;mol/Ti(OC_3H_7)_4\;mol$)를 42로 하여 수열합성법으로 이산화티탄 졸을 제조하였다. 축산폐수에 대한 이산화티탄 광촉매 반응은 이산화티탄, UV가 모두 존재할 경우가 단독으로 존재할 경우보다 활성이 증가하였고, 축산폐수의 pH가 산성일 때 활성이 우수한 것으로 나타났다. 또한, 이산화티탄 광촉매 반응은 자외선의 세기, 광촉매의 량, 공기 주입량, 과산화수소의 주입량이 증가함에 따라 활성도가 증가하였으나 과산화수소의 량이 일정수준 이상에서는 오히려 활성의 감소가 일어났다.

• 한국생물공학회:학술대회논문집
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• 한국생물공학회 2005년도 생물공학의 동향(XVI)
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• pp.272-276
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• 2005

음식물 폐기물을 3단계 메탄발효 공정을 이용하여 처리하였을 때 배출되는 발효폐액은 거의 액상으로 고농도의 sCOD, T-N and $NH_{3}-N$를 함유하고 있다. 본 연구에서는 3단계 메탄 발효 후 최종 유출되는 고농도의 유기성 폐수를 물리${\cdot}$화학적 응집 및 침전을 이용하여 전처리 한 후 고효율 자외선/광촉매 시스템을 이용하여 후속 처리를 하고자 하였다. $FeCl_{3}$를 이용하여 전처리하였을 때 최적 pH 및 농도는 4와 2000 mg/L로 52.6%의 COD제거율을 보였다. 고효율 자외선/광촉매 시스템의 경우 24시간 동안 COD는 2890 mg/L에서 184 mg/L로 감소하였으며, T-N은 2496 mg/L에서 914 mg/L로 감소하였다.

• 청정기술
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• 제11권3호
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• pp.123-128
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• 2005

$TiO_2$는 금속 산화물의 일종으로서 자체가 가지고 있는 물리화학적 안정성, 무독성, 탁월한 유기물의 산화분해력 등으로 인해 저농도의 환경 유해물질 정화 분야로 응용이 활발히 연구되고 있는 반도체 물질이다. 그러나 $TiO_2$는 자외선 영역대(${\lambda}$ < 387 nm, 태양광의 2.7%가 UV)의 빛을 통해서 활성을 나타내고, 여기된 전자의 빠른 전자-정공 재결합속도로 인해 광 효율이 저하되는 단점을 갖는다. 따라서 광 감응 파장대를 넓히고 재결합속도를 길게 함으로써 광효율을 높이고, 광촉매 활성을 증대하는 방향으로 연구의 초점이 모아지고 있는 실정이다. 본 연구에서는 $TiO_2$ 광촉매의 광 감응 파장대를 가시광선 영역으로 확대함과 동시에 여기된 전자와 정공의 재결합시간을 연장하기 위하여 백금(Pt)이 광침적(photodeposition)된 탄소(C) 도핑 $TiO_2$를 제조하였다. 제조한 $Pt-C-TiO_2$의 특성은 전자투과현미경(Transmission Electron Microscopic; TEM), 질소흡탈착법(Brunauer-Emmett-Teller method; BET), X-ray 회절 분석법(X-ray Diffractometer; XRD), 분광 산란 광도계(UV-visible diffuse reflectance spectroscopy; UV-Vis DRS), X-ray 광전자 광도계(X-ray Photoelectron Spectroscopy; XPS)를 통하여 살펴보았다. $Pt-C-TiO_2$의 광촉매 활성을 검증하기 위하여 아조 계열의 붉은색 염료인 Acid Red 44 ($C_{10}H_7N=NC_{10}H_3(SO_3Na)_2OH$)의 광분해 실험을 수행하였다. 광원은 Xe arc 램프(300 W, Oriel)를 사용하였으며 420 nm 이하 제거 필터를 사용하여 가시광 영역대의 빛만을 조사되도록 하였다. 그 결과, 제조한 $Pt-C-TiO_2$는 가시광선 하에서 사용제품과 비교하여 월등히 뛰어난 분해력을 보이며 $C-TiO_2$의 활성을 한 층 더 향상시킴을 확인하였다. 이는 무한 에너지 자원인 태양광을 이용한 염료 폐수 정화 시스템 응용으로의 유용한 결과라 할 수 있겠다.

• 한국환경보건학회지
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• 제31권5호
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• pp.415-422
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• 2005

The photocatalytic decolorization of Reactive Red 2B(RR2B) was studied using immobilized photocatalyst/UV System. Two pairs of 20 W UV-B and UV-C lamps were employed as the light source. Immobilization of $TiO_2$ was carried out using sponge (as the photocatalyst body) and silicone sealant(as the binder). The effects of parameters such as the thickness, pore size of sponge photocatalyst and attached material on the reactor bottom were investigated. The results showed that the optimum thickness of sponge photocatalyst was 1 cm. Decolorization of reactor which had the bottom coated $TiO_2$ was higher than that of reactor attached aluminum plate. Decolorization of photocatalyst with large pore size(mean pore size, 3.8 mm) was higher than that of the small(mean pore size, 1.75 mm). Initial decolorization of RR2B could be descrived using the Langmuir-Hinshelwood(L-H) model and gave constant values of $0.55mg/l{\cdot}min(k)\;and\;2.65{\times}10^{-2}l/mg(K)$, respectively.

• 한국전기전자재료학회:학술대회논문집
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• 한국전기전자재료학회 2006년도 추계학술대회 논문집 광주전남지부
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• pp.39-42
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• 2006

Titania sols or powders were are very promising materials for environment as photocatalyst. The band gap energy of $TiO_2$ has been known to be 2.8 to 3.2 eV. But the measuring system of its band gap is usually depend on absorption properties. Thus, in this study, absorption properties of $TiO_2$ sols prepared by hydrothermal process were researched with the effect of various particle sizes and concentrations. The mean particle size in $TiO_2$ sols increased as 15 nm to 60 nm, absorption graph measured by UV-Vis spectrometer shows to move red-shift. When dilute solution added with $2^n$ in $TiO_2$, the band gap energy increases as linear function.