• Proceedings of the Korean Society of Soil and Groundwater Environment Conference
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• 1999.10a
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• pp.99-102
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• 1999

본 연구에서는 대표적인 물리 화학적 토양정화방법인 토양세척기법의 효율증진을 위하여, Fe를 다량 함유한 고농도 윤활유 오염토양을 대상으로 알카리 용액과 산성용액의 세척효율을 비교 검토하고, 과산화수소의 첨가에 따른 세척효율의 향상효과를 알아보았다. 세척용제인 NaOH와 HCl를 이용하여 세척효율 검토 결과 NaOH를 이용한 경우에 약 60% 의 세척효율을 나타냈다. 또한 NaOH 농도에 따른 정화 효율은 각각 0.5% > 1% $\geq$ 2% 순서로 증가하였다. 기존의 세척효율을 향상시키기 위하여 과산화수소를 첨가하고 오염토양의 정화효율을 비교 검토한 결과 NaOH용액에서는 과산화수소의 농도가 증가할수록 정화효율이 증가하였으나 NaOH의 농도증가에 대해서는 큰 영향을 보이지 않았으며, NaOH 3%의 농도에서 과산화수소 1%를 첨가했을 때 85%의 정화효율을 나타냈다. 또한 과산화수소 주입시기에 따른 영향을 검토한 결과 세척 후 과산화수소를 주입한 경우에 정화효율이 높았다. 반면에 HCl의 경우는 HCl의 농도가 증가할수록 정화효율이 증가하였고, 세척하지 않고 과산화수소를 주입한 경우에 정화효율이 증가하였다. 고농도의 윤활유 오염토양의 세척효율을 증진시키기 위한 처리로서 과산화수소의 주입은 NaOH 상태에서 그 효율이 약 15%정도 증진되었으며, 일정시간에 이르면 정화효율이 평형에 도달하는 것을 알 수 있었다. HCl 상태에서는 25%의 정화효율이 증진되는 것을 알 수 있었다.

• Proceedings of the Korean Environmental Sciences Society Conference
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• 2008.11a
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• pp.443-446
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• 2008

본 연구는 과산화수소를 이용하여 디젤오염토양의 처리시 중금속 용출특성, 백연가스 발생특성 등을 평가하기 위하여 실험을 하였다. 중금속 용출속도는 반응시간 15분까지 용출이 지속적으로 증가하다가, 15분 이후 점차적으로 감소하는 경향을 보였다. 이러한 과산화수소(H$_2$O$_2$) 처리방법은 토양내 중금속 용출속도를 가속화시켜 실제 현장에서 적용될 경우 이로 인하여 지하수에 심각한 영향을 미칠 수 있으므로 ex-situ 방법 등과 같은 방법을 고려한 2차 오염에 대한 대책이 필요할 것으로 판단된다. 또한, 백연가스의 발생량은 과산화수소의 농도가 높을수록 많이 발생하는 것으로 관찰되었으며, 이는 높은 농도의 과산화수소와 유류오염토양이 급격하게 반응하기 때문인 것으로 판단된다. 백연가스 중 Hexane이 가장 높은 농도로 검출되었으며, 이 외에도 Cyclopentane, Benzene, Ethylbenzene, m,p-Xylene, Undecane 등이 많이 발생하는 것으로 나타났다. 따라서 백연가스 중에 함유된 고농도의 휘발성유기화합물(VOCs)이 주변 환경에 유해한 영향을 미칠 것으로 예상되므로 적절한 대기오염방지시설을 설치하여 제거한 후 대기로 방출하는 것이 필요하다고 판단된다.

• Proceedings of the Korean Vacuum Society Conference
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• 2013.02a
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• pp.541-541
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• 2013

현재 병원에서 사용하는 치아미백은 고농도의 과산화수소와 carbamide peroxide가 함유된 미백제를 이용하여 전문성을 가진 의사가 직접 시술을 하고 있다 [1]. 과산화수소의 농도가 높을수록 미백효과가 높지만 [2] 과산화수소의 농도가 지나치게 높으면 인체에 유해하다 [3,4]. 따라서, 고농도의 과산화수소가 함유된 미백제의 사용은 전문가만 시술할 수 있도록 이를 제한하고 있다. 이로 인해, 일반 가정용으로 판매되는 다양한 미백제품들은 저농도(최대6%)의 과산화수소가 함유되어 있으며 장기간 지속적으로 사용해야만 치아미백효과를 볼 수 있다. 우리는 가정에서도 보다 안전하고 단기간에 효율적으로 치아의 미백효과를 보기 위하여, 식품의약품안정청에서 규제하고 있는, carbamide peroxide (15%)와 저온 대기압 플라즈마 제트를 사용하여 미백효과를 관찰하였다. 플라즈마 제트의 유량은 200 sccm이며, 공기를 사용하였다. 미백효과를 보기 위한 대상으로는 우치(牛齒)를 사용하였으며, 플라즈마를 처리하여 미백효과를 관찰하였다. 실험 대조시료군으로는 carbamide peroxide (15%)를 처리하지 않은 우치와 처리한 우치, 그리고 carbamide peroxide (15%)를 처리한 우치에 수증기(0.2~1%)를 첨가한 다음, 이들 세가지 시료에 각각 공기 플라즈마를 조사하여 비교해보았다. 모든 실험의 플라즈마 처리시간은 최대 20분까지로 하였다. 수증기를 첨가한 이유는 활성산소의 농도를 높이기 위함이며, 이로써 탁월한 미백효과를 얻을 수 있다. 이는 활성산소와 치아의 유기질이 반응하여, 색이 진한 탄소고리 화합물을 밝은 색의 사슬구조로 바꿔주기 때문이다. 실험을 통하여 우치에 carbamide peroxide (15%)와 수증기(0.2~1%)를 처리한 경우 플라즈마의 미백효과가 탁월함을 보였다. 이때 CIE색좌표 ($L^*a^*b^*$)에서 명도도가 최대 2배 이상 높아짐을 보았다. 미백효과에 대한 측정은 측색분광기(CM-3500d)를 이용하였다.

• Korean Journal of Microbiology
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• v.31 no.2
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• pp.166-174
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• 1993

Streptomyces coeUc%r (Muller) cells were treated with $100 \mu$M hydrogen peroxide for I hour and proteins synthesized during hydrogen peroxide stress were labeled with L-[$^{35}S$]-methionine. Total cellular proteins were extracted and analyzed by two-dimensional polyacrylamide gel electrophoresis. In exponential growth phase, synthesis of about 100 proteins was increased by hydrogen peroxide treatment. These proteins were named as Pin (£eroxide-inducib]e) proteins and classified into 4 subgroups according to their induction time after hydrogen peroxide treatment. About 60 of them were found to be induced within 20 minutes and maintained throughout I hour of treatment. In stationary growth phase. synthesis of 62 proteins was increased by hydrogen peroxide and 21 of them were the same Pins found in exponential growth phase. Proteins from the mutants which are resistant to hydrogen peroxide were obtained in exponential growth phase and compared with those from the wild type on two-dimensional gel. The three mutants, N7, N9. and N24, were found to have higher constitutive leve]s of ]5, 17, and 15 Pin proteins respectively, than the wild type. 9 of these Pin proteins (D74.7a, E76.0c, E23.3. F50.7, F47.2a. F25.5, G39.6b, G24.0, H39.6a) increased in two of the three mutants and 3 proteins (F39.7, H6I.7. 120.8) increased in all of the three mutants. These proteins might play important roles in the response of S. coelic%r to hydrogen peroxide.

• Analytical Science and Technology
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• v.18 no.2
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• pp.112-119
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• 2005

This study reports on the efficiency of cleaning enameled magnet wire using a sulfuric acid $H_2SO_4$ and removal of dissolved organic material using hydrogen peroxide $H_2O_2$ and nitric acid $HNO_3$ at $80^{\circ}C$. The method involves the addition of pure $H_2SO_4$ and $H_2O_2$ or $HNO_3$. Layers of enameled organic material were dissolved by 90% $H_2SO_4$ and the solution was maintained as 35% $H_2O_2$ or 60% $HNO_3$. $H_2O_2$ content in aqueous $H_2O_2$ was maintained as 8.8 : 1.0. An initial concentration of $H_2SO_4$ in dissolution conditions was accomplished within 15 min, with a stripping time of about 2 h. The concentrations of $H_2O_2$ and $HNO_3$ in the processing bath were relatively low, but sufficient enough to produce an effective amount of power in the bath for the removal of the enamel material. The cleaning effect of enameled organic material involves the dehydration by $H_2SO_4$ and the oxidation by $H_2O_2$ or $HNO_3$.

• Journal of Korean Society of Environmental Engineers
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• v.35 no.12
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• pp.889-896
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• 2013

Advanced Oxidation Processes (AOP) have been interested for removing micropollutants in water. Most of water treatment plants (WTPs) located along the lower part of Nakdong River have adopted the $O_3/BAC$ process and have interesting in peroxone process a kind of AOP. This study evaluated the removal characteristics of residual hydrogen peroxide ($H_2O_2$) combining with the biofiltration process in the next BAC process when the hydrogen peroxide is applied for the WTP operating $O_3/BAC$ process. In the experiment, changing the temperature and the concentration of $H_2O_2$ of influent, the biofiltration process showed rapidly dropped the biodegradability when the $H_2O_2$ concentration was increased and lowered water temperature while BAC process maintained relatively stable efficiency. The influent fixed at $20^{\circ}C$ and the concentration of $H_2O_2$ at 300 mg/L was continuously input for 78 hours. Most of the $H_2O_2$ in the influent did not remove at the biofiltration process controlled 5 to 15 minutes EBCT condition after 24~71 hours operating time while BAC process controlled 5 to 15 minutes EBCT showed 38~91% removal efficiency condition after 78 hours operating time. Besides, after 78 hours continuously input experiment, the biomass and activity of attached bacterial on the biofilter and BAC were $6.0{\times}10^4CFU/g$, $0.54mg{\cdot}C/m^3{\cdot}hr$ and $0.4{\times}10^8CFU/g$, $1.42mg{\cdot}C/m^3{\cdot}hr$ respectively. These biomass and activity values were decreased 99% and 72% in biofilter and 68% and 53% in BAC compared with initial condition. The biodegradation rate constant ($k_{bio}$) and half-life ($t_{1/2}$) in BAC were decreased from $1.173min^{-1}$ to $0.183min^{-1}$ and 0.591 min to 3.787 min respectively according to increasing the $H_2O_2$ concentration from 10 mg/L to 300 mg/L at $5^{\circ}C$ water temperature and the $k_{bio}$ and $t_{1/2}$ were $1.510min^{-1}$ to $0.498min^{-1}$ and 0.459 min to 1.392 min at $25^{\circ}C$ water temperature. By increasing the water temperature from $5^{\circ}C$ to $15^{\circ}C$ or $25^{\circ}C$, the $k_{bio}$ were increased 1.1~2.1 times and 1.3~4.4 times. If a water treatment plant operating $O_3/BAC$ process is considering the hydrogen peroxide for the peroxone process, post BAC could effectively decrease the residual $H_2O_2$, moreover, in case of spilling the $H_2O_2$ into the water process line, these spilled $H_2O_2$ concentration can be able to decrease by increasing the EBCT at the BAC process.

• Journal of Korea Soil Environment Society
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• v.2 no.3
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• pp.49-57
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• 1997

Naturally-occurring iron minerals, goethite and magnetite, were used to catalyze hydrogen peroxide and initiate Fenton-like oxidation of silica sand contaminated with diesel, kerosene in batch systems. Reaction conditions were investigated by varying H$_2$0$_2$concentration(0%, 1%, 15%), initial contaminant concentration(0.2, 0.5, 1.0g diesel and kerosene/kg soil), and iron minerals(1, 5wt% magnetite or goethite). Contaminant degradations in silica sand-iron mineral-$H_2O$$_2$ systems were identified by determining total petroleum hydrocarbon(TPH) concentration. In case of silica sand contaminated with diesel(1g contaminan/kg soil with 5wt% magnetite) addition of 0%, 1%, 15% of $H_2O$$_2$showed 0%, 25%, and 60% of TPH reduction in 8 days, respectively When the mineral contents were varied from 1 to 5wt%, removal of contaminants increased by 16% for magnetite and 13.1% for goethite. The results from system contaminated by kerosene were similar to those of the diesel. Reaction of magnetite system was more aggressive than that of goethite system due to dissolution of iron and presence of iron(II) and iron(III); however, dissolved iron precipitated on the surface of iron mineral and seemed to cause reducing electron transfer activity on the surface and quenching $H_2$$O_2$. The system used goethite has better treatment efficiency due to less $H_2$$O_2$ consumption. Results of this study showed possible application of catalyzed $H_2$$O_2$ system to petroleum contaminated site without addition of iron source since natural soils generally contain iron minerals such as magnetite and goethite.

• Journal of Animal Environmental Science
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• v.15 no.3
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• pp.209-216
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• 2009

The aim of this study was to investigate the removal effects of the color, nutritive salts and other pollutants on piggery slurry by advanced oxidation process (AOP) system. The experimental AOP system was designed to treat 300 L of piggery slurry per hour. To enhance oxidizing power of the experimental APO system, a ultraviolet irradiation system and the ultrasonic system were attached to the AOP system. With 5 min ultrasonic treatment, COD, SS and T-N concentrations were changed from 210, 820, and 309 to 200, 760, and 262 mg/L, respectively. With 10 min ultrasonic treatment, SS and T-N concentrations tended to decrease but T-P concentration was not changed. With the treatment of both ozone and ultrasonic waves for 30 min, COD, SS, T-N and T-P decreased from 238, 900, 400, and 5 to 165, 540, 263, and 4 mg/L, respectively. With the treatment of both ozone and ultraviolet irradiation for 30 min, COD, SS, T-N and T-P decreased from 321, 340, 204, and 15 to 151, 140, 111, and 7 mg/L, respectively, and color was changed from 4,344 to 624.

• Journal of dental hygiene science
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• v.17 no.6
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• pp.481-486
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• 2017

The study aimed to compare the whitening efficacy of a strip and gel containing 2.9% hydrogen peroxide, using a tooth whitening light activator. The whitening effect was compared through in vitro and in vivo studies. In the in vitro study, we used stained hydroxyapatite (HAP) specimens as artificial teeth. HAP specimens were made using HAP powder and polyvinyl alcohol solution, and stained by modified Stookey's method. A whitening gel and whitening strip were applied to the respective specimens for 20 minutes, with a light activator. The color changes were measured using a colorimeter. In the in vivo study, one group (test 1) used the gel with a light activator and the other group (test 2) used a strip with the same activator for 15 minutes a day, for four consecutive days. An organoleptic evaluation using a Vita shade guide and instrumental evaluation using a Shade eye-NCC (Shofu Co., Japan) were performed. The color change values (${\Delta}E^*$) in the in vitro study revealed the strip with the light activator to be more effective than the gel with the same activator (p<0.001). In the in vivo study, even though there was no significant difference between the groups with respect to the ${\Delta}E^*$, using either the Shade eye-NCC or the Vita shade guide, the change in yellowness (${\Delta}b^*$) was statistically significant (p=0.024). In conclusion, test 2 group that used 2.9% hydrogen peroxide strip with a light activator, showed a tendency towards increased whitening than test 1 group that used the gel with the same activator; however further studies are needed to validate the above finding.

• Journal of the korean academy of Pediatric Dentistry
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• v.34 no.1
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• pp.1-12
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• 2007

The purpose of this study was to evaluate the effect that various concentration and application time of hydrogen peroxide had on tooth whitening and physical properties. The hydroxyapatite (HA) discs of $12mm({\Phi}){\times}1.2mm(t)$ in dimensions were made by compression $(100kg/cm^2)$ and sintering (at $1350^{\circ}C$ for 2 hours) All specimens were polished sequentially with '240 through '2000 emery paper and one side of each specimen was polished finally with $0.3{\mu}m$ alumina paste. The discs were placed in sterile whole stimulated saliva overnight at $37^{\circ}C$ in order to form an in vitro pellicle layer. Then the discs were rinsed with distilled water and soaked into staining broth at $37^{\circ}C$ for 7 days. These stained specimens were bleached with hydrogen peroxide according to the change of concentration $(3{\sim}30%)$ and application time ($3{\sim}10$ days). The specimens were analyzed with a spectrophotometer, X-ray diffractometer (XRD), scanning electron microscope (SEM), surface roughness tester, microhardness tester and biaxial flexural strength. The results of present study can be summarized as follows : 1. The bleaching effect was increased with the increased concentration and the extended application time of hydrogen peroxide. 2. The surface roughness was significantly increased from the specimen bleached with 15% hydrogen peroxide for 10 days and with 30% for 7 and 10 days respectively (p<0.05). 3. The changes of crystal phase observed by XRD between before and after bleaching weren't shown of any difference, but microporous structure of surface observed by SEM was shown of increase with the increased concentration and the extended application. 4. The biaxial flexural strength was significantly decreased from bleaching of specimen with 30% hydrogen peroxide for 7 and 10 days respectively (p<0.05) 5. Microhardness was significantly decreased from bleaching with 15% hydrogen peroxide for 10 days and with 30% for 3, 7 and 10 days respectively (p<0.05). Although the tooth bleaching effect was greater when the high concentration was applied, further in vivo experiment will be needed to prove it's safety.