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| 93625-14-0

中文名称
——
中文别名
——
英文名称
——
英文别名
——
化学式
CAS
93625-14-0
化学式
C2F5O
mdl
——
分子量
135.013
InChiKey
SKQFZBKPXBDELV-UHFFFAOYSA-N
BEILSTEIN
——
EINECS
——
  • 物化性质
  • 计算性质
  • ADMET
  • 安全信息
  • SDS
  • 制备方法与用途
  • 上下游信息
  • 反应信息
  • 文献信息
  • 表征谱图
  • 同类化合物
  • 相关功能分类
  • 相关结构分类

计算性质

  • 辛醇/水分配系数(LogP):
    2.2
  • 重原子数:
    8
  • 可旋转键数:
    0
  • 环数:
    0.0
  • sp3杂化的碳原子比例:
    0.5
  • 拓扑面积:
    9.2
  • 氢给体数:
    0
  • 氢受体数:
    6

反应信息

  • 作为反应物:
    描述:
    乙烯正庚烷 为溶剂, 反应 0.33h, 生成
    参考文献:
    名称:
    Komendantov, A. M.; Sass, V. P.; Sokolov, S. V., Journal of Organic Chemistry USSR (English Translation), 1986, vol. 22, p. 439 - 441
    摘要:
    DOI:
  • 作为产物:
    描述:
    五氟二甲基醚 作用下, 21.85 ℃ 、93.33 kPa 条件下, 反应 1.0h, 生成
    参考文献:
    名称:
    Atmospheric degradation mechanism of CF3OCF2H
    摘要:
    Smog chamber/FTIR techniques were used to study the Cl atom initiated oxidation of CF3OCF2H in 700 Torr of N-2/O-2 at 295 +/- 2 K. Atmospheric oxidation of CF3OCF2H proceeds via the formation of CF3OCF2 radicals. The atmospheric fate of CF3OCF2 radicals is addition Of O-2 to give CF3OCF2O2 radicals. In the atmosphere CF3OCF2O, radicals are converted via COF2 and CF3OH into CO2 and HF. Relative rate techniques were used to measure k(Cl + CF3OCF2H) = (2.3 +/- 0.3) x 10(-17) cm(3) molecule(-1) s(-1). The results are discussed with respect to the atmospheric degradation and environmental impact of CF3OCF2H. (C) 2001 Elsevier Science B.V. All rights reserved.
    DOI:
    10.1016/s0009-2614(01)00698-4
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文献信息

  • Komendantov, A. M.; Sass, V. P.; Sokolov, S. V., Journal of Organic Chemistry USSR (English Translation), 1986, vol. 22, p. 439 - 441
    作者:Komendantov, A. M.、Sass, V. P.、Sokolov, S. V.
    DOI:——
    日期:——
  • Atmospheric degradation mechanism of CF3OCF2H
    作者:Y. Inoue、M. Kawasaki、T.J. Wallington、M.D. Hurley
    DOI:10.1016/s0009-2614(01)00698-4
    日期:2001.8
    Smog chamber/FTIR techniques were used to study the Cl atom initiated oxidation of CF3OCF2H in 700 Torr of N-2/O-2 at 295 +/- 2 K. Atmospheric oxidation of CF3OCF2H proceeds via the formation of CF3OCF2 radicals. The atmospheric fate of CF3OCF2 radicals is addition Of O-2 to give CF3OCF2O2 radicals. In the atmosphere CF3OCF2O, radicals are converted via COF2 and CF3OH into CO2 and HF. Relative rate techniques were used to measure k(Cl + CF3OCF2H) = (2.3 +/- 0.3) x 10(-17) cm(3) molecule(-1) s(-1). The results are discussed with respect to the atmospheric degradation and environmental impact of CF3OCF2H. (C) 2001 Elsevier Science B.V. All rights reserved.
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