首页> 外文期刊>The journal of physical chemistry, A. Molecules, spectroscopy, kinetics, environment, & general theory >Atmospheric Chemistry of the Phenoxy Radical, C_6H_5O(·): UV Spectrum and Kinetics of Its Reaction with NO, NO_2, and O_2
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Atmospheric Chemistry of the Phenoxy Radical, C_6H_5O(·): UV Spectrum and Kinetics of Its Reaction with NO, NO_2, and O_2

机译:苯氧自由基C_6H_5O(·)的大气化学:UV光谱及其与NO,NO_2和O_2反应的动力学

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摘要

Pulse radiolysis and FT-IR smog chamber experiments were used to investigate the atmospheric fate of C_6H_5O(·) radicals. Pulse radiolysis experiments gave σ(C_6H_5O(·))_(235 nm) = (3.82 ± 0.48) * 10~(-17) cm~2 molecule~(-1), k(C_6H_5O(·) + NO) = (1.88 ± 0.16) * 10~(-12), and k(C_6H_5O(·) + NO_2) = 2.08 ± 0.15 * 10~(-12) cm~3 molecule~(-1) s~(-1) at 296 K in 1000 mbar of SF_6 diluent. No discernible reaction of C_6H_5O(·) radicals with O_2 was observed in smog chamber experiments, and we derive an upper limit of k(C_6H_5O(·) + O_2) < 5 * 10~(-21) cm~3 molecule~(-1) s~(-1) at 296 K. These results imply that the atmospheric fate of phenoxy radicals in urban air masses is reaction with NO_x. Density functional calculations and gas chromatography-mass spectrometry are used to identify 4-phenoxyphenol as the major product of the self-reaction of C_6H_5O(·) radicals. As part of this study, relative rate techniques were used to measure rate constants for reaction of Cl atoms with phenol [k(Cl + C_6H_5OH) = (1.93 ± 0.36) * 10~(-10)], several chlorophenols [k(Cl + 2-chlorophenol) = (7.32 ± 1.30) * 10~(12), k(Cl + 3-chlorophenol) = (1.56 ± 0.21) * 10~(10), and k(Cl + 4-chlorophenol) = (2.37 ± 0.30) * 10~(-10)], and benzoquinone [k(Cl + benzoquinone) = (1.94 ± 0.35) * 10~(-10)], all in units of cm~3 molecule~(-1) s~(-1). A reaction between molecular chlorine and C_6H_5OH to produce 2- and 4-chlorophenol in yields of (28 ± 3)% and (75 ± 4)% was observed. This reaction is probably heterogeneous in nature, and an upper limit of k(Cl_2 + C_6H_5OH) ≤ 1.9 * 10~(-20) cm~3 molecule~(-1) s~(-1) was established for the homogeneous component. These results are discussed with respect to the previous literature data and to the atmospheric chemistry of aromatic compounds.
机译:利用脉冲辐射分解和红外光谱烟雾室实验研究了C_6H_5O(·)自由基的大气归宿。脉冲辐射分解实验得出σ(C_6H_5O(·))_(235 nm)=(3.82±0.48)* 10〜(-17)cm〜2分子〜(-1),k(C_6H_5O(·)+ NO)=( 1.88±0.16)* 10〜(-12),k(C_6H_5O(·)+ NO_2)= 2.08±0.15 * 10〜(-12)cm〜3分子〜(-1)s〜(-1)在296 K在1000 mbar的SF_6稀释剂中。在烟雾室实验中未观察到C_6H_5O(·)自由基与O_2的可辨别反应,我们得出k(C_6H_5O(·)+ O_2)<5 * 10〜(-21)cm〜3分子〜(- 1)在296 K时s〜(-1)。这些结果表明,城市空气中苯氧基自由基的命运是与NO_x反应。密度泛函计算和气相色谱-质谱法用于鉴定4-苯氧基苯酚是C_6H_5O(·)自由基自反应的主要产物。作为这项研究的一部分,使用相对速率技术来测量Cl原子与苯酚[k(Cl + C_6H_5OH)=(1.93±0.36)* 10〜(-10)],几种氯酚[k(Cl + 2-氯苯酚)=(7.32±1.30)* 10〜(12),k(Cl + 3-氯苯酚)=(1.56±0.21)* 10〜(10),k(Cl + 4-氯苯酚)=( 2.37±0.30)* 10〜(-10)]和苯醌[k(Cl +苯醌)=(1.94±0.35)* 10〜(-10)],均以cm〜3分子〜(-1)为单位s〜(-1)。观察到分子氯与C_6H_5OH之间的反应,生成2-和4-氯苯酚,产率为(28±3)%和(75±4)%。该反应本质上可能是异质的,并且为均质组分确定了k(Cl_2 + C_6H_5OH)≤1.9 * 10〜(-20)cm〜3分子〜(-1)s〜(-1)的上限。关于先前的文献数据和芳族化合物的大气化学讨论了这些结果。

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