Suppr超能文献

异氟烷、地氟烷和七氟烷的大气化学:与氯原子和 OH 自由基的反应动力学和机理及全球变暖潜能。

Atmospheric chemistry of isoflurane, desflurane, and sevoflurane: kinetics and mechanisms of reactions with chlorine atoms and OH radicals and global warming potentials.

机构信息

Jet Propulsion Laboratory, California Institute of Technology, 4800 Oak Grove Drive, Mail Stop 183-901, Pasadena, California 91109, United States.

出版信息

J Phys Chem A. 2012 Jun 21;116(24):5806-20. doi: 10.1021/jp2077598. Epub 2011 Dec 6.

Abstract

The smog chamber/Fourier-transform infrared spectroscopy (FTIR) technique was used to measure the rate coefficients k(Cl + CF(3)CHClOCHF(2), isoflurane) = (4.5 ± 0.8) × 10(-15), k(Cl + CF(3)CHFOCHF(2), desflurane) = (1.0 ± 0.3) × 10(-15), k(Cl + (CF(3))(2)CHOCH(2)F, sevoflurane) = (1.1 ± 0.1) × 10(-13), and k(OH + (CF(3))(2)CHOCH(2)F) = (3.5 ± 0.7) × 10(-14) cm(3) molecule(-1) in 700 Torr of N(2)/air diluent at 295 ± 2 K. An upper limit of 6 × 10(-17) cm(3) molecule(-1) was established for k(Cl + (CF(3))(2)CHOC(O)F). The laser photolysis/laser-induced fluorescence (LP/LIF) technique was employed to determine hydroxyl radical rate coefficients as a function of temperature (241-298 K): k(OH + CF(3)CHFOCHF(2)) = (7.05 ± 1.80) × 10(-13) exp[-(1551 ± 72)/T] cm(3) molecule(-1); k(296 ± 1 K) = (3.73 ± 0.08) × 10(-15) cm(3) molecule(-1), and k(OH + (CF(3))(2)CHOCH(2)F) = (9.98 ± 3.24) × 10(-13) exp[-(969 ± 82)/T] cm(3) molecule(-1); k(298 ± 1 K) = (3.94 ± 0.30) × 10(-14) cm(3) molecule(-1). The rate coefficient of k(OH + CF(3)CHClOCHF(2), 296 ± 1 K) = (1.45 ± 0.16) × 10(-14) cm(3) molecule(-1) was also determined. Chlorine atoms react with CF(3)CHFOCHF(2) via H-abstraction to give CF(3)CFOCHF(2) and CF(3)CHFOCF(2) radicals in yields of approximately 83% and 17%. The major atmospheric fate of the CF(3)C(O)FOCHF(2) alkoxy radical is decomposition via elimination of CF(3) to give FC(O)OCHF(2) and is unaffected by the method used to generate the CF(3)C(O)FOCHF(2) radicals. CF(3)CHFOCF(2) radicals add O(2) and are converted by subsequent reactions into CF(3)CHFOCF(2)O alkoxy radicals, which decompose to give COF(2) and CF(3)CHFO radicals. In 700 Torr of air 82% of CF(3)CHFO radicals undergo C-C scission to yield HC(O)F and CF(3) radicals with the remaining 18% reacting with O(2) to give CF(3)C(O)F. Atmospheric oxidation of (CF(3))(2)CHOCH(2)F gives (CF(3))(2)CHOC(O)F in a molar yield of 93 ± 6% with CF(3)C(O)CF(3) and HCOF as minor products. The IR spectra of (CF(3))(2)CHOC(O)F and FC(O)OCHF(2) are reported for the first time. The atmospheric lifetimes of CF(3)CHClOCHF(2), CF(3)CHFOCHF(2), and (CF(3))(2)CHOCH(2)F (sevoflurane) are estimated at 3.2, 14, and 1.1 years, respectively. The 100 year time horizon global warming potentials of isoflurane, desflurane, and sevoflurane are 510, 2540, and 130, respectively. The atmospheric degradation products of these anesthetics are not of environmental concern.

摘要

烟雾箱/傅里叶变换红外光谱(FTIR)技术用于测量速率系数 k(Cl + CF(3)CHClOCHF(2), 异氟烷) = (4.5 ± 0.8) × 10(-15), k(Cl + CF(3)CHFOCHF(2), 地氟烷) = (1.0 ± 0.3) × 10(-15), k(Cl + (CF(3))(2)CHOCH(2)F, 七氟烷) = (1.1 ± 0.1) × 10(-13), 和 k(OH + (CF(3))(2)CHOCH(2)F) = (3.5 ± 0.7) × 10(-14) cm(3) molecule(-1)在 700 Torr 的 N(2)/空气稀释剂中 295 ± 2 K。Cl + (CF(3))(2)CHOC(O)F 的 k 值上限为 6 × 10(-17) cm(3) molecule(-1)。激光光解/激光诱导荧光(LP/LIF)技术用于确定羟基自由基速率系数作为温度的函数(241-298 K):k(OH + CF(3)CHFOCHF(2)) = (7.05 ± 1.80) × 10(-13) exp[-(1551 ± 72)/T] cm(3) molecule(-1); k(296 ± 1 K) = (3.73 ± 0.08) × 10(-15) cm(3) molecule(-1),和 k(OH + (CF(3))(2)CHOCH(2)F) = (9.98 ± 3.24) × 10(-13) exp[-(969 ± 82)/T] cm(3) molecule(-1); k(298 ± 1 K) = (3.94 ± 0.30) × 10(-14) cm(3) molecule(-1)。k(OH + CF(3)CHClOCHF(2), 296 ± 1 K) = (1.45 ± 0.16) × 10(-14) cm(3) molecule(-1)的速率系数也被确定。氯原子通过 H 提取与 CF(3)CHFOCHF(2)反应生成 CF(3)CFOCHF(2)和 CF(3)CHFOCF(2)自由基,产率约为 83%和 17%。CF(3)C(O)FOCHF(2)烷氧基自由基的主要大气命运是通过消除 CF(3)来分解,生成 FC(O)OCHF(2),不受生成 CF(3)C(O)FOCHF(2)自由基的方法影响。CF(3)CHFOCF(2)自由基添加 O(2),并通过后续反应转化为 CF(3)CHFOCF(2)O 烷氧基自由基,其分解生成 COF(2)和 CF(3)CHFO 自由基。在 700 Torr 的空气中,82%的 CF(3)CHFO 自由基通过 C-C 断裂生成 HC(O)F 和 CF(3)自由基,其余 18%与 O(2)反应生成 CF(3)C(O)F。(CF(3))(2)CHOCH(2)F 的大气氧化生成 CF(3)C(O)FOCHF(2)的摩尔产率为 93 ± 6%,CF(3)C(O)CF(3)和 HCOF 为次要产物。CF(3))(2)CHOC(O)F 和 FC(O)OCHF(2)的红外光谱首次被报道。CF(3)CHClOCHF(2)、CF(3)CHFOCHF(2)和(CF(3))(2)CHOCH(2)F(七氟烷)的大气寿命分别估计为 3.2、14 和 1.1 年。异氟烷、地氟烷和七氟烷的 100 年时间跨度全球变暖潜能值分别为 510、2540 和 130。这些麻醉剂的大气降解产物没有环境问题。

文献AI研究员

20分钟写一篇综述,助力文献阅读效率提升50倍。

立即体验

用中文搜PubMed

大模型驱动的PubMed中文搜索引擎

马上搜索

文档翻译

学术文献翻译模型,支持多种主流文档格式。

立即体验