• Title/Summary/Keyword: Methane amount

Search Result 303, Processing Time 0.024 seconds

Atomic bonding structure in the a-C:H thin films prepared by ECR-PECVD (ECR-PECVD 방법으로 제조한 a-C:H 박막의 결합구조)

  • 손영호;정우철;정재인;박노길;김인수;배인호
    • Journal of the Korean Vacuum Society
    • /
    • v.9 no.4
    • /
    • pp.382-388
    • /
    • 2000
  • Hydrogenated amorphous carbon (a-C:H) films were fabricated by electron cyclotron resonance plasma-enhanced chemical vapor deposition. The bonding structure of carbon and hydrogen in the a-C:H films has been investigated by varying the deposition conditions such as ECR power, gas composition of methane and hydrogen, deposition time, and negative DC self bias voltage. The bonding characteristics of the a-C:H thin film were analyzed using FTIR spectroscopy. The IR absorption peaks of the film were observed in the range of $2800\sim3000 \textrm{cm}^{-1}$. The atomic bonding structure of a-C:H film consisted of $sp^3$ and $sp^2$ bonding, most of which is composed of $sp^3$ bonding. The structure of the a-C:H films changed from $CH_3$ bonding to $CH_2$ or CH bonding as deposition time increased. We also found that the amount of dehydrogenation in a-C:H films was increased as the bias voltage increased.

  • PDF

The Characterization of Woodchip Torrefaction and Byproduct Gas (우드칩 반탄화와 부생가스의 특성 분석)

  • Kang, Ku;Wang, Long;Hong, Seong Gu
    • Journal of The Korean Society of Agricultural Engineers
    • /
    • v.56 no.6
    • /
    • pp.55-62
    • /
    • 2014
  • Torrefaction is considered as a promising pre-treatment for thermochemical utilization of biomass. Torrefaction temperature and time are the critical operation parameters. In this study, investigated were the effects of reaction temperature and time on product composition of torrefaction. scanning electron microscope (SEM) images and thermo gravimetric analyzer (TGA) results were also compared for the effects of the operating parameters. SEM images showed that the pores were observed at the temperature of $250^{\circ}C$ for 30 minutes. Rapid decreases in weight were observed the temperature between 200 and$400^{\circ}C$. Higher heating value of the torrefied biomass was over 5,000 kcal/kg at the temperature of $250^{\circ}C$ for 45 minutes. Energy density, which is defined as the ratio of the energy yield over the mass yield was 1.36 at the temperature of $250^{\circ}C$ for 45 minutes. The energy density was higher up to 1.6 at the temperature of $280^{\circ}C$, which indicates greater loss in mass. The major components of the gas produced in the torrefaction were $CO_2$ and CO, with traces of methane. The total amount of gas was 31.54 l/kg and the calorific value of the gas was $1,164.4Kcal/Nm^3$ at the temperature of $250^{\circ}C$ for 30 minute reaction time. Based on the results of this study, the temperature of effective torrefaction is about $250^{\circ}C$ for 30 to 45 minutes of reaction time. Considering the heating value, it is desirable to utilize the gas for efficient process of torrefaction.

Bias-enhanced Nucleation of Diamond in Hot Filament CVD (열필라멘트 CVD에서 전압 인가에 의한 다이아몬드의 핵생성 촉진)

  • Choi, Kyoon;Kang, Suk-Joong L.;Hwang, Nong-M.
    • Journal of the Korean Ceramic Society
    • /
    • v.34 no.6
    • /
    • pp.636-644
    • /
    • 1997
  • The effect of various processing parameters, in particular the substrate and filament temperature, on the nucleation of diamond has been studied for the hot filament CVD process with a negative bias on the substrate. As far as the substrate temperature was maintained around the critical temperature of 73$0^{\circ}C$, the nucleation of diamond increased with increasing filament temperature. The maximum nucleation density of ~ 2$\times$109/$\textrm{cm}^2$ was obtained under the condition of filament temperature of 230$0^{\circ}C$, substrate temperature of 75$0^{\circ}C$, bias voltage of 300V, methane concentration of 20%, and deposition time of 2 hours. This nucleation density is about the same as those obtained in previous investigations. For fixed substrate temperatures, the nucleation density varies up to about 103 times depending on experimental conditions. This result is different from that of Reinke, et al. When the substrate temperature was above 80$0^{\circ}C$, a silkworm~shaped carbon phase was co-deposited with hemispherical microcrystalline diamond, and its amount increased with increasing substrate temperature. The Raman spectrum of the silkworm-shaped carbon was the same as that of graphitic soot. The silkworm-shaped carbon was etched and disappeared under the same as that of graphitic soot. The silkworm-shaped carbon was etched and disappeared under the deposition condition of diamond, implying that it did not affect the nucleation of diamond.

  • PDF

The Study on Characteristics of a-C:H Films Deposited by ECR Plasma (전자회전공명 플라즈마를 이용한 a-C:H 박막의 특성 연구)

  • 김인수;장익훈;손영호
    • Proceedings of the Korea Society for Industrial Systems Conference
    • /
    • 2001.05a
    • /
    • pp.224-231
    • /
    • 2001
  • Hydrogenated amorphous carbon films were deposited by ERC-PECVD with deposition conditions, such as ECR power, gas composition of methane and hydrogen, deposition time, and substrate bias voltage. The characteristics of the film were analyzed using the AES, ERDA, FTIR. Raman spectroscopy and micro hardness tester. From the results of AES and ERDA, the elements in the deposited film were confirmed as carbon and hydrogen atoms. FTIR spectroscopy analysis shows that the atomic bonding structure of a-C:H film consisted of sp³and sp²bonding, most of which is composed of sp³bonding. The structure of the a-C:H films changed from CH₃bonding to CH₂or CH bonding as deposition time increased. We also found that the amount of dehydrogenation in a-C:H films was increased as the bias voltage increased. Raman scattering analysis shows that integrated intensity ratio (I/sub D//I/sub G/) of the D and G peak was increased as the substrate bias voltage increased, and films hardness was increased.

  • PDF

Effect of the additive gas on the bonding structure and mechanical properties of the DLC films deposited by RF-PECVD (RF-PECVD법에 의해 증착된 DLC 박막의 결합구조와 기계적 특성에 관한 보조가스의 영향)

  • Choi, Bong-Geun
    • Journal of the Korean Crystal Growth and Crystal Technology
    • /
    • v.25 no.4
    • /
    • pp.145-152
    • /
    • 2015
  • In this work, we were investigated the effect of the additive gases on the relationship between bonding structure and mechanical properties of the deposited films when the DLC films were deposited on Si-wafer by the rf-PECVD method with the addition of small amounts of carbon dioxide and nitrogen to the mixture gas of methane and hydrogen. The deposition rate of the films increased as the rf-power increased, while it decreased with increasing the amount of additive gases. Also, as the carbon dioxide gas increased, the hydrogen content in the films decreased but the $sp^3/sp^2$ ratio of the films increased. In case of nitrogen gas, the hydrogen content decreased, however the $sp^3/sp^2$ ratio and nitrogen gas flow rate did not show a specific tendency.

Synthesis of Indoline tri-isopropyl benzene sulfonamide as a potential new asymmetric catalyst (새로운 술폰아미드계의 촉매의 합성)

  • Yun, In-Gwon;Kim, Hwan-Cheol
    • The Journal of Natural Sciences
    • /
    • v.7
    • /
    • pp.47-51
    • /
    • 1995
  • In order to develope new asymmetric catalyst, we synthesized the following new sulfonamide derivatives start from S-Indoline-2-Carboxylic Acid via the following 5 steps. Hydroxy methyl derivative(1) was thus treated with methane sulfonyl chloride in the presence of triethylamine as base to give mesylated derivative(2) in 85% of isolated yield. The mesylate compound (2) was treated with excess sodium azide to give Azido derivative (4) in 95% isolated yield. Azido compound (3) was then reduced to the corresponding amino derivative in near quntitative yield by the hydrogenation under hydrogen atmospere in the presence of catalytic amount of Pd-C. The amino derivative (4) was converted to its sulfonamide derivatives by the treatment of compound(4) with triisopropyl benzene sulfonyl chloride in the presence of triethyl amine as base. Finally t-BOC group of the compound(5) was removed by the treatement of excess Trifluoro-acetic acid in near quantitative yield to give the target sulfonamide derivative (7) .in this paper we prepared compound(6) in 49% overall yield via the 5 steps of synthesis starting from t-Boc- 2-hydroxy methyl indoline(1) which cab be easily prepared from commercial available S-indoline-2-carboxylic acid by known methods. we plan to apply this new catalyst for the asymmetric reduction , diels-alder reaction, aldolcondensation reaction in due courses.

  • PDF

Characteristics of Carbon Dioxide Gasification for Sewage Sludge in Microwave (마이크로웨이브에 의한 하수 슬러지 이산화탄소 가스화 특성)

  • JEONG, BYEORI;YOON, SOOHYUK;CHUN, YOUNGNAM
    • Transactions of the Korean hydrogen and new energy society
    • /
    • v.27 no.2
    • /
    • pp.192-200
    • /
    • 2016
  • A characteristics of microwave drying-gasification was analyzed for converting a dewatered sewage sludge generated a wastewater treatment plant. Gas (60%) was the largest component of the product of microwave gasification, followed by sludge char (33%) and tar (2%). The main components of the producer gas were hydrogen (33%) and carbon monoxide (40%), and there was some methane and hydrocarbons ($C_2H_4$, $C_2H_6$, $C_3H_8$). Larger nitrogen and smaller oxygen amounts were generated. Gravimetric tar generated $414g/m^3$. This means a total tar which is a heavy hydrocarbons from the volatile organic substance in the sewage sludge. Selected light tars were benzene, anthracene, naphthalene, pyrene, showing lower concentrations as 2.62, 0.37, 0.49, $0.28g/m^3$, respectively. Sludge char has larger meso pores which is a mean pore size of $50.85{\AA}$ and has high adsorptivity. An amount of adsorption was $228.71cm^3/g$, showing higher quantity than acommercial adsorbers. This indicates that the gas obtained from the microwave gasification of wet sewage sludge can be used as fuel, but the heavy tar in the gas must be treated. Sludge char can be used as a tar reduction adsorbent in the process, and then burns as a solid fuel.

A Study on the Reaction Optimization for the Utilization of CO2 and CH4 from Bio-gas (바이오가스에서 CO2/CH4 활용에 관한 반응최적화 연구)

  • KHO, DONGHYUN;CHO, WOOKSANG;BAEK, YOUNGSOON
    • Transactions of the Korean hydrogen and new energy society
    • /
    • v.27 no.5
    • /
    • pp.554-561
    • /
    • 2016
  • Depending on the Bio-gas sources, main component gases of $CH_4$ and $CO_2$ are shown to be variously present in amounts. For the anaerobic digester, The concentration of $CH_4$ and $CO_2$ in the gases are 60~70 and 30~35 vol%. For the landfill gas, $CH_4$ and $CO_2$ are 40~60 and 40~60 vol%. For the food wastes, $CH_4$ and $CO_2$ are 60~80 and 20~40 vol%, respectively. In this study, maximum conversion rates of $CO_2$ were obtained from the variety of concentrations of $CH_4$ and $CO_2$ by the catalysts of reforming reactions. Moreover, in order to get maximum producing amount of synthetic gas, experimental studies were performed to optimize the reaction variables. On the basis of $CH_4$, 243 ml, R [$CH_4/(O2+CO_2)$] value were varied from 0.8 to 1.35, in the study of $CH_4$ and $CO_2$ reforming reactions. It was shown that the optimal results were obtained for 1.35 of R value. And also, at $850^{\circ}C$ and 1 atm, the production rate of synthetic gas was 90% and the conversion rates of $CH_4$ and $CO_2$ were higher than 99% and 90%, respectively.

Analysis of statistical models on temperature at the Seosan city in Korea (충청남도 서산시 기온의 통계적 모형 연구)

  • Lee, Hoonja
    • Journal of the Korean Data and Information Science Society
    • /
    • v.25 no.6
    • /
    • pp.1293-1300
    • /
    • 2014
  • The temperature data influences on various policies of the country. In this article, the autoregressive error (ARE) model has been considered for analyzing the monthly and seasonal temperature data at the northern part of the Chungcheong Namdo, Seosan monitoring site in Korea. In the ARE model, five meteorological variables, four greenhouse gas variables and five pollution variables are used as the explanatory variables for the temperature data set. The five meteorological variables are wind speed, rainfall, radiation, amount of cloud, and relative humidity. The four greenhouse gas variables are carbon dioxide ($CO_2$), methane ($CH_4$), nitrous oxide ($N_2O$), and chlorofluorocarbon ($CFC_{11}$). And the five air pollution explanatory variables are particulate matter ($PM_{10}$), sulfur dioxide ($SO_2$), nitrogen dioxide ($NO_2$), ozone ($O_3$), and carbon monoxide (CO). The result showed that the monthly ARE model explained about 39-63% for describing the temperature. However, the ARE model will be expected better when we add the more explanatory variables in the model.

Emission Characteristics of Greenhouse Gases (CH4, N2O) in Mechanically Ventilated Swine Farm during Winter Season (겨울철 강제환기식 돈사 내 온실가스 (CH4, N2O) 배출 특성 연구)

  • Park, Junyong;Jung, Minwoong;Jo, Gwanggon;Jang, Yu-Na
    • Journal of The Korean Society of Agricultural Engineers
    • /
    • v.63 no.4
    • /
    • pp.33-41
    • /
    • 2021
  • The emission characteristics and emission factors were determined by measuring the concentration of methane (CH4) and nitrous oxide (N2O), the amount of ventilation, etc. in the two fattening rooms which have the same environment in winter. As a result of monitoring, the average concentration of CH4 and N2O was 20.7-26.7 ppm and 1.4-1.6 ppm. The average temperature inside the room was measured at 20.0-21.4℃, and the average ventilation was 1345.4-1567.3 m3/h. The daily emission of CH4 for the first 30 days showed a constant emission of 3.6-8.2 g/d/m2/pig, but thereafter, the emission increased rapidly. The daily emission of N2O was 0.7-1.3 g/d/m2/pig, showing stable emission during the test period, and relatively insignificant emission compared to the emission of CH4. After repeated test, it was confirmed that there was no significant difference between the two rooms. As a result, the CH4 6. 21 g/d/m2/pig and N2O 1.02 g/d/m2/pig average emission for each room was derived.