• Title/Summary/Keyword: Gas phase reaction

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A Study on Soil Washing for Diesel-contaminated Soil by using Decomposition of NaOH/H$_2$O$_2$ (디젤유로 오염된 토양의 NaOH/H$_2$O$_2$ 분해를 이용한 토양세척에 관한 연구)

  • Hwang, Jong-Hyun;Choi, Won-Joon;Kim, Min-Chul;Jung, Jong-Hyeon;Ha, Soo-Ho;Oh, Kwang-Joong
    • Journal of Korean Society of Environmental Engineers
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    • v.30 no.10
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    • pp.999-1005
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    • 2008
  • The main reaction for soil washing with using sodium hydroxide(NaOH) and hydrogen peroxide(H$_2$O$_2$) was desorption and flotation of petrochemical contaminant by means of oxygen bubble. We found the rate of decomposition by rate constant according to various temperature. For the purpose of optimizing the operation factor, we examined the effect of concentration of NaOH and H$_2$O$_2$, washing time, and soil:water ratio. The rate of decomposition for H$_2$O$_2$ in liquid phase is the first order reaction by its concentration. The rate constant of k$_1$ was 0.9439 $\times$ exp(-1376.82/RT) when concentration of NaOH was lower than 0.1 M, and the rate constant of k$_2$ was 17.3588 $\times$ exp(-2320.06/RT) when it was higher than NaOH of 0.1 M. It found that NaOH was facilitated at the beyond of specific concentration. We confirmed the optimum concentration of NaOH/H$_2$O$_2$ by means of rate constants during soil washing. Also, the optimum conditions during soil washing were washing time of 15 min, soil : water ratio of 1 : 3, and NaOH/H$_2$O$_2$ concentration of 0.25 M/0.1 M.

Partial Oxidation of CH4 Using {0.7}Sr0.3Ga0.6Fe0.4O3-δ for Soild Oxide Fuel Cell (고체산화물 연료전지용 La0.7Sr0.3Ga0.6Fe0.4O3-δ계의 메탄부분산화반응)

  • Lee, Seung-Young;Lee, Kee-Sung;Lee, Shi-Woo;Kim, Jong-Won;Woo, Sang-Kuk
    • Journal of the Korean Electrochemical Society
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    • v.6 no.1
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    • pp.59-64
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    • 2003
  • We fabricated mixed ionic-electronic conducting membranes, $CH_4\;Using\;{0.7}Sr_{0.3}Ga_{0.6}Fe_{0.4}O_{3-\delta}$, by solid state reaction method for solid oxide fuel cell. The membranes consisted of single perovskite phase and exhibited high relative density, $>95\%$. We coated $La_{0.6}Sr_{0.4}CoO_{3-\delta}$ layer using screen printing method in order to improve surface reactivity of the $La_{0.7}Sr_{0.3}Ga_{0.6}Fe_{0.4}O_{3-\delta}$. As a result, the oxygen permeation flux of the coated $La_{0.7}Sr_{0.3}Ga_{0.6}Fe_{0.4}O_{3-\delta}$ showed higher value, $0.5ml/min{\cdot}cm^2\;at\;950^{\circ}C$ than the uncoated one. Higher oxygen permeation was observed in the porously coated Lao $La_{0.7}Sr_{0.3}Ga_{0.6}Fe_{0.4}O_{3-\delta}$membranes with larger grain sizes. Syngas, $CO+H_2$, was successfully obtained from methane gas, $CH_4$, using the $La_{0.6}Sr_{0.4}CoO_{3-\delta}$ coated $La_{0.7}Sr_{0.3}Ga_{0.6}Fe_{0.4}O_{3-\delta}$, with over $40\%\;of\;CH_4$ conversion and syngas yield. $La_{0.7}Sr_{0.3}Ga_{0.6}Fe_{0.4}O_{3-\delta}$ membrane was stable even when it was exposed to the reducing environment, methane, for 600 hrs at $950^{\circ}C$.

Simultaneous Oxidation of NO, CO, and CH4 over Mn-Cu/Al2O3 Catalyst (Mn-Cu/Al2O3 촉매 상에서 NO, CO 및 CH4 동시 산화)

  • Ji Eun Jeong;Chang-Yong Lee
    • Applied Chemistry for Engineering
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    • v.35 no.1
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    • pp.1-7
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    • 2024
  • Mn-M/Al2O3 (M = Cu, Fe, Co, and Ce) catalysts were prepared for simultaneous oxidation of NO, CO, and CH4, and their oxidation activities were compared. The Mn-Cu/ Al2O3 catalyst with the best simultaneous oxidation activity was characterized by XRD, Raman, XPS, and O2-TPD analysis. The result of XRD indicated that Mn and Cu existed as complex oxides in the Mn-Cu/Al2O3 catalyst. Raman and XPS results showed that electron transfer between Mn ions and Cu ions occurred during the formation of the Mn-O-Cu bond in the Mn-Cu/Al2O3 catalyst. The XPS O 1s and O2-TPD analyses showed that the Mn-Cu/Al2O3 catalyst has more adsorbed oxygen species with high mobility than the Mn/Al2O3 catalyst. The high simultaneous oxidation activity of the Mn-Cu/Al2O3 catalyst is attributed to these results. Gas-phase NO promotes the oxidation reactions of CO and CH4 in the Mn-Cu/Al2O3 catalyst while suppressing the NO oxidation reaction. These results were presumed to be because the oxidized NO was used as an oxidizing agent for CO and CH4. On the other hand, the oxidation reactions of CO and CH4 competed on the Mn-Cu/Al2O3 catalyst, but the effect was not noticeable because the catalyst activation temperature was different.