• 한국표면공학회지
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• 제33권4호
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• pp.281-288
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• 2000

To understand the effect of Fe on the oxidation behavior of TiAl alloys, TiAl-(2, 4, 6at% )Fe were oxidized at 800 and 90$0^{\circ}C$ in air. The oxidation resistance of TiAl-Fe alloys increased with increasing an iron content. The scales formed consisted of an outer $TiO_2$ layer, an intermediate $A1_2$$O_3$ layer, and an inner mixed ($TiO_2$+$A1_2$$O_3$) layer, being similar to other common TiAl alloys. But, the scales formed on TiAl-Fe alloys were generally thin compared to those formed on pure TiAl, and contained dissolved iron. Below the oxide scale, an oxygen affected zone was formed. This beneficial effects of Fe on increasing the oxidation resistance and scale adherence of TiAl alloys were attributed to the refinement of oxide grains, increased scale adherence and the enhanced alumina-forming tendency.

• 한국표면공학회:학술대회논문집
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• 한국표면공학회 1999년도 춘계학술발표회 초록집
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• pp.11-12
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• 1999

• Bulletin of the Korean Chemical Society
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• 제28권5호
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• pp.843-846
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• 2007

• 한국수소및신에너지학회논문집
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• 제17권1호
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• pp.21-30
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• 2006

[ $M/Fe_2O_3$ ] (M=Rh, Ce and Zr) mixed oxides were prepared using urea method to develop a medium for chemical hydrogen storage by their redox cycles. And their redox behaviors by repeated cycles were studied using temperature programmed reaction(TPR) technique. Additives such as Rh, Ce and Zr were added to iron oxides in order to lower the reaction temperature for reduction by hydrogen and re-oxidation by water-splitting. From the results, concentration of urea used as a precipitant had little effect on particle size and reduction property of iron oxide. TPR patterns of iron oxide consisted of two reduction peaks due to the course of $Fe_2O_3\;{\rightarrow}\;Fe_3O_4\;{\rightarrow}\;Fe$. The results of repeated redox tests showed that Rh added to iron oxide have an effect on lowering the re-oxidation temperature by water-splitting. Meanwhile, Ce and Zr additives played an important role in prevention of deactivation by repeated cycles. Finally, Fe-oxide(Rh, Ce, Zr) sample added with Rh, Ce and Zr showed the lowest re-oxidation temperature by water-splitting and maintained high $H_2$ recovery in spite of the repeated redox cycles. Consequently, it is expected that Fe-oxide(Rh, Ce, Zr) sample can be a feasible medium for chemical hydrogen storage using redox cycle of iron oxide.

• 한국수산과학회지
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• 제35권2호
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• pp.162-165
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• 2002

백색육어를 배소한 경우와 배소한 시료를 저온에 저장 후, 단계적으로 가열처리했을 때 일어나는 산화에 의한 heme 화합물의 변화를 조사하였다. Heme 화합물 중 myoglobin 함량은 각시가자미나 조기 모두 180$^{\circ}C$에서 20분간 어피 제거육의 상태로 배소한 것이 상대적으로 감소폭이 컸으며 가열, 재가열에 의해서도 감소하는 경향이었다. Myoglobin의 감소 추세에 따라 metmyoglobin 함량은 역으로 점차 증가하는 경향이었으며, 배소온도가 낮을수록 또한 어피를 제거함으로써 생성된 metmyoglobin의 함량이 높았다. 총철 함량은 배소온도와 시간을 달리하여 처리하여도 두 어종 모두 생시료와는 함량 차이가 거의 없었다. 비 heme 철은 각시가자미의 경우 생시료에는 총철함량에 대해 약 $20\%$ 정도 함유되어 있었으나, 180$^{\circ}C$에서 20분간 어피 제거육의 상태로 배소했을 경우 생시료에 비해 약 2배 정도 증가하였다. 조기는 생시료에는 건물당으로 약 0.8mg/100g 함유되어 있었으나 배소, 가열 및 재가열과 같은 반복되는 가열과정에 의해 증가하였다. Heme 철 함량은 각시가자미와 조기 모두 비 heme 철의 증가에 반비례해서 감소하였으며 또한 배소시간이 길수록 그리고 어피 잔존육보다는 어피 제거육의 감소폭이 더 컸다.

• 한국토양환경학회지
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• 제2권3호
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• pp.49-57
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• 1997

천연 토양 속에 많이 존재하는 철광식인 goethite, magnetite와 과산화수소수를 이용해 펜톤 유사 반응(Fenton-like oxidation)을 유도하여 디젤과 등유로 각각 오염된 모래(silica sand)를 회분식 시스템으로 처리하여 보았다. 과산화수소수의 농도(0%, 1%, 15%), 초기 오염물의 농도(0.2, 0.5, 1.0g디젤, 등유/kg 모래), 그리고 철광석(iron minerals)의 양(0, 1, 5wt% magnetite or goethite)을 달리하여 반응조건들을 조사하였다. 모래-철광석-$H_2O$$_2$system에서의 오염물의 분해는 잔존 Total Petroleum Hydrocarbon(TPH)의 농도를 분석하여 확인하였다. 디젤이 silica sand에 오염된 경우(1.0g오염물/kg soil, 5wt% magnetite)에 과산화수소수의 농도를 0%, 1%, 그리고 15%로 달리하여 본 결과 8일후 각각 0%, 25%, 60%의 TPH 감소를 보였다. 철광석의 양이 lwt%에서 5wt%로 증가되었을 경우, 오염물의제거량이 magnetite의 경우 16%, goethite의 경우 13.1%만큼 증가하였다. 등유가 사용된 경우에 있어서의 오염물 분해는 디젤이 사용된 경우와 비슷하게 나타났다. Magnetite system은 iron(II)과 iron(III)이 공존하며, 미량의 철성분이 용해되므로 goethite system보다 오염물의 분해가 더 많이 일어나는 것으로 보인다. 그러나 용해된 철성분은 철광석 표면에 침전물의 형태로 쌓이게 되어 철광석 표면의 전자교환능력을 감소시키고 과산화수소수를 quenching시키는 것으로 사료된다. 그리하여 goethite system에서 과산화수소수가 적게 소모되어 magnetite system보다 나은 처리효율을 가지는 것으로 나타났다. 이 연구의 결과를 통하여 볼 때 천연토양속에는 magnetite와 goethite같은 철광석이 함유되어 있으므로 별도의 철성분 첨가없이 과산화수소수의 처리만으로도 석유로 오염된 토양의 처리가 가능할 것으로 보인다.

• 한국표면공학회지
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• 제51권2호
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• pp.104-109
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• 2018

Fe-2 wt.%Ni alloys were fabricated by metal powder injection molding, and their oxidation behavior at $600-700^{\circ}C$ for 30 h in air was studied in order to find the effect of the small addition of Ni in the iron matrix on the high-temperature oxidation. Oxide scales that formed after oxidation consisted primarily of $Fe_2O_3$, where microscopic voids were scattered. Nickel was segregated initially at the scale/matrix interface, and later at the lower part of the $Fe_2O_3$ scale. At $600^{\circ}C$, Fe-2wt.%Ni alloys oxidized parabolically initially, and linearly after 15 h. At $650-700^{\circ}C$, they oxidized linearly from the initial period. Although Fe-2wt.%Ni alloys oxidized slower than pure iron, their oxidation rates were relatively fast.

• Bulletin of the Korean Chemical Society
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• 제23권3호
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• pp.369-373
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• 2002

The liquid phase oxidation of p-xylene has been carried out with oxygen-enriched gas, and the manganese component was precipitated probably via over-oxidation to $Mn^{4+}$. The precipitation increased with rising oxygen concentration in the reaction gas and occurred mainly in the later part of the oxidation. The activity of the reaction decreased, and the blackening of the product and side reactions to carbon dioxide increased with the degree of precipitation. Precipitation can be decreased with the addition of metal ions, such as cerium, chromium and iron.

• 한국환경보건학회지
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• 제24권3호
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• pp.63-69
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• 1998

The treatment of soils and water contaminated with MTBE using the Fenton oxidation was investigated. The effects of dosage of $H_{2}O_{2}$, and Fe$^{2+}$ concentrations, and solution pH on transformation and mineralization in soil were evaluated. Generation of TBA and acetone following Fenton-oxidation of MTBE in water and generation of acetone following Fenton-oxidation of TBA were observed. Therefore TBA and acetone are degradation intermediates of MTBE. There was a large difference of treatment efficiency in Fenton oxidation of MTBE between soil and water system. This may be caused by the complex nature of soil, soil organic matter which can consumed OH $\cdot$ radicals, and interacting with inorganic-soil constituents. The pH of soil was observed to have a significant effect on the chemical oxidation efficient of MTBE in soil The data demonstrated that optimal pH range were pH 3~4 and around 6. The soil batch studies demonstrated that treatment efficiency of MTBE was enhanced by adding additional ferrous salts but Fenton-oxidation occurred in no additional iron which indicated that iron in soil can catalyze the Fenton-oxidation. The most effective parameter of Fentonoxidation was $H_{2}O_{2}$/Fe$^{2+}$ ratio which theocratical ratio is 0.5. The optimal range of this ratio was found to be 0.6~2.3. In evaluating effect of $H_{2}O_{2}$ dosage on treatment efficiency, the increase of $H_{2}O_{2}$ did not always lead to increase of decompositions of MTBE in soil. Fenton oxidation was effective in destroying MTBE in aqueous extracts of contaminated soil and water. Experimental data provided evidence that the Fenton oxidation can effectively remediate MTBE-contaminated water and soil.

• 한국재료학회지
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• 제26권4호
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• pp.187-193
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• 2016

Fabrication of iron oxide/carbon nanotube composite structures for detection of ammonia gas at room temperature is reported. The iron oxide/carbon nanotube composite structures are fabricated by in situ co-arc-discharge method using a graphite source with varying numbers of iron wires inserted. The composite structures reveal higher response signals at room temperature than at high temperatures. As the number of iron wires inserted increased, the volume of carbon nanotubes and iron nanoparticles produced increased. The oxidation condition of the composite structures varied the carbon nanotube/iron oxide ratio in the structure and, consequently, the resistance of the structures and, finally, the ammonia gas sensing performance. The highest sensor performance was realized with $500^{\circ}C/2h$ oxidation heat-treatment condition, in which most of the carbon nanotubes were removed from the composite and iron oxide played the main role of ammonia sensing. The response signal level was 62% at room temperature. We also found that UV irradiation enhances the sensing response with reduced recovery time.