Karagulian Federico, Scott Lea A, Dilbeck Christopher W, Finlayson-Pitts Barbara J
Department of Chemistry, University of California, Irvine, CA 92697-2025, USA.
Phys Chem Chem Phys. 2008 Jan 28;10(4):528-41. doi: 10.1039/b712715d. Epub 2007 Dec 4.
The ozonolysis of an approximately one monolayer film of 1-oleoyl-2-palmitoyl-sn-glycero-3-phosphocholine (OPPC) on NaCl was followed in real time using diffuse reflection infrared Fourier transform spectrometry (DRIFTS) at 23 degrees C. Matrix-assisted laser desorption/ionization (MALDI) mass spectrometry and Auger electron spectroscopy were used to confirm the identification of the products. Ozone concentrations ranged from 1.7 x 10(12) to 7.0 x 10(13) molecules cm(-3) (70 ppb to 2.8 ppm). Upon exposure to O3, there was a loss of C[double bond, length as m-dash]C accompanied by the formation of a strong band at approximately 1110 cm(-1) due to the formation of a stable secondary ozonide (1,2,4-trioxolane, SOZ). The yield of the SOZ was smaller when the reaction was carried out in the presence of water vapor at concentrations corresponding to relative humidities between 2 and 25%. The dependencies of the rate of SOZ formation on the concentrations of ozone and water vapor are consistent with the initial formation of a primary ozonide (1,2,3-trioxolane, POZ) that can react with O3 or H2O in competition with its thermal decomposition to a Criegee intermediate and aldehyde. Estimates were obtained for the rate constants for the POZ thermal decomposition and for its reactions with O3 and H2O, as well as for the initial reaction of O3 with OPPC. The SOZ decomposed upon photolysis in the actinic region generating aldehydes, carboxylic acids and anhydrides. These studies show that the primary ozonide has a sufficiently long lifetime when formed on a solid substrate that direct reactions with O3 and H2O can compete with its thermal decomposition. In dry polluted atmospheres, ozone-alkene reactions may lead in part to the formation of stable secondary ozonides whose chemistry, photochemistry and toxicity should be taken into account in models of such regions.
在23摄氏度下,使用漫反射红外傅里叶变换光谱法(DRIFTS)实时跟踪了1-油酰基-2-棕榈酰基-sn-甘油-3-磷酸胆碱(OPPC)在氯化钠上约一个单分子层薄膜的臭氧分解过程。使用基质辅助激光解吸/电离(MALDI)质谱和俄歇电子能谱来确认产物的鉴定。臭氧浓度范围为1.7×10¹²至7.0×10¹³个分子·厘米⁻³(70 ppb至2.8 ppm)。暴露于O₃后,C═C键消失,同时由于形成稳定的二级臭氧化物(1,2,4-三氧杂环戊烷,SOZ),在约1110厘米⁻¹处形成一条强带。当反应在水蒸气存在下进行时,SOZ的产率较小,水蒸气浓度对应于2%至25%的相对湿度。SOZ形成速率对臭氧和水蒸气浓度的依赖性与初级臭氧化物(1,2,3-三氧杂环戊烷,POZ)的初始形成一致,该初级臭氧化物可以与O₃或H₂O反应,与其热分解为克里奇中间体和醛相竞争。获得了POZ热分解及其与O₃和H₂O反应的速率常数估计值,以及O₃与OPPC的初始反应速率常数估计值。SOZ在光化区域光解时分解,生成醛、羧酸和酸酐。这些研究表明,初级臭氧化物在固体基质上形成时具有足够长的寿命,以至于与O₃和H₂O的直接反应可以与其热分解相竞争。在干燥的污染大气中,臭氧-烯烃反应可能部分导致形成稳定的二级臭氧化物,在这些区域的模型中应考虑其化学、光化学和毒性。