• Journal of the Korean Ceramic Society
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• v.36 no.2
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• pp.167-171
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• 1999

Titanium dioxide bodies sintered at 130$0^{\circ}C$ for 10 h under the oxygen flowing were reduced with hydrogen in 1200, 1250 and 130$0^{\circ}C$ for 4~20 h. Reduction kinetics were evaluated by measuring a weight loss between before and after reduction, and the thickness of reduced layer, respectively. The reduction followed the parabolic rate law, indicating that the rate-determining process is diffusion. From the Arrhenius plots, the apparent activation energies for the reduction were obtained as 210$\pm$10 kJ/mol.

• Proceedings of the Korea Water Resources Association Conference
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• 2015.05a
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• pp.284-284
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• 2015

본 연구는 퍼클로레이트의 생물학적 환원 과정에 있어서 고농도의 염이 미생물에게 어떤 영향을 미치는지를 다양한 방법을 통해서 알아보고 적절한 모델링 접근을 통하여 최적 환원속도를 위한 반응조 조건 및 설계에 필요한 요소들을 도출하기 위해 수행되었다. 100mL 합성폐수를 포함하는 플라스크를 이용한 실험이 수행되었고, 일정 농도의 퍼클로레이트와 유일 탄소원으로 아세트산나트륨이 사용되었다. 염화나트륨 농도가 $7490{\mu}s/cm$에서 $23700{\mu}s/cm$까지 증가하는 동안 퍼클로레이트의 생물학적 환원 속도는 현저하게 감소하였으며, $32100{\mu}s/cm$ 이상의 염화나트륨 농도에서는 퍼클로레이트가 환원되지 않았다. 동일한 농도의 염화나트륨, 염화암모늄, 염산 및 황산이 포함된 하수에서는 퍼클로레이트의 환원속도가 모두 비슷하였다.

• Proceedings of the Materials Research Society of Korea Conference
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• 2007.11a
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• pp.115.2-115.2
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• 2007

• Proceedings of the Korean Institute of Surface Engineering Conference
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• 2012.11a
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• pp.191-191
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• 2012

유체 플라즈마 공정(SPP)은 고에너지를 가지는 플라즈마를 유체 내에 발생시키는 공정으로서 나노유체 및 촉매 물질 제조 등 여러 가지 응용분야에 적용할 수 있다. 본 연구에서는 SPP 공정을 이용하여 금 나노입자를 합성하였고 전압과 방전시간의 변화에 따른 금나노 입자의 환원속도를 분석하였다.

• Resources Recycling
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• v.20 no.4
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• pp.71-77
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• 2011

$MoO_3$ powders were reduced to $MoO_2$ under Ar+$H_2$ gas mixture in a tubular furnace at temperature range 723~873 K. Reaction rate was quantitatively deduced by measuring relative humidity of off gas. Observed reaction rate increased significantly with hydrogen partial pressure and reaction temperature and the rate of $H_2O$ evolution increased drastically during the initial period of reduction. As reduction proceeded, however, $H_2O$ partial pressure decreased noticeably. During the initial period of the reduction, a linear relationship for time dependence of the reduction fraction was observed. The activation energy for the reduction of $MoO_3$ to $MoO_2$was 73.56 kJ/mol during the initial period of reduction.

• Proceedings of the Korean Nuclear Society Conference
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• 1998.10a
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• pp.270-270
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• 1998

• Proceedings of the KSEEG Conference
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• 2002.04a
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• pp.444-447
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• 2002

• Economic and Environmental Geology
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• v.36 no.1
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• pp.39-48
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• 2003

The removal of chromate from aqueous solution using finely ground pyrite and biotite was investigated by batch experiments and the kinetics and the mechanism of chromate reduction were discussed. The chromate reduction by pyrite was about hundred times faster than that by biotite and was also faster at pH 3 than at pH 4. When pyrite was used, more than 90% of initial chromate was reduced within four hours at pH 4 and within 40 min. at pH 3. However, more than 400 hours was taken for the reduction of 90% of initial chromate by biotite. The results indicate that the rate of chromate reduction was strongly depending on the amount of Fe(II) in the minerals and on the dissolution rate of Fe(II) from the minerals. The reduction of chromate at pH 4 resulted in the precipitation of (Cr, Fe)(OH))$_3$$_{ (s)}$, which is believed to have limited the concentrations of dissolved Cr(III) and Fe(III) to less than expected values. When biotite was used, amounts of decreased Fe(II) and reduced Cr(Ⅵ) did not show stoichiometric relationship, which implying there was not only chromate reduction by ferrous ions in the acidic solution but also heterogeneous reduction of ferric ions by the structural ferrous iron in biotite. However, the results from a series of the experiments using Pyrite showed that concentrations of the decreased Fe(II) and the reduced Cr(Ⅵ) were close to the stoichiometric ratio of 3:1. It was because the oxidation of pyrite rapidly created ferrous ions even in oxygenated solutions and the chromate reduction by the ferrous ions was significantly faster than ferrous ion oxygenation.

• Resources Recycling
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• v.7 no.1
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• pp.34-40
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• 1998

This shdy was invcsligated on reduction rate of EAF dust wth solid carbon cantents. The rate equation for reduction ofEAF dust was obtaincd in the tempcrahlrc range cot 910-108O"C, and the ratio of zinc removal and metallization raho of ironoxides to thc reaction time was also analysed. From the XRD analysis for slag residues '||'&'||'er reaction, the cxistcncc DI themixture of Akemmite[Ca2MgSi2O.] and SiO, was identified.ed.

• Resources Recycling
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• v.11 no.4
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• pp.37-43
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• 2002

As the consumption of galvanized steels in cans and automobiles and the quantity of scraps increase, the recycling problems of EAF dust become a important problem. Valuable metals such as Fe, Zn, Pb are of continued interest to metallurgists. To recover the valuable metal and to remove the toxicity of EAF dust, high temperature smelting process is or researching as a pilot scale. The Reduction kinetics of Zn in EAF dust is so important in a view of the economic consideration of the process. In this study, the kinetics behavior of Zn in EAF dust were measured as a point of application in high temperature smelting process. The rate control step in ZnO and franklinite is revealed to be chemical reaction on the reaction surface.