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Heterogeneous chemistry in the troposphere: The nitric acid 'renoxification'.

机译:对流层中的非均相化学:硝酸“重新氧化”。

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The current observed discrepancy between the field and modeled NO x/HNO3 ratios suggests that chemistry that may affect the oxidative capacity of the atmosphere remains unidentified. We studied several heterogeneous reactions involving HNO3 and various atmospheric species (NO, CO, CH4 and SO2) proposed to reconcile these ratios.; The BET surface area of several atmospherically available natural and anthropogenic surfaces was determined to evaluate the potential role in heterogeneous chemistry. The BET surface area of these surfaces was 3 to 5 orders of magnitude higher than the geometric surface area of the samples. Silica was chosen as the proxy surface of atmospherically available surfaces, and its interaction with water using a combination of FTIR and BET theory was studied. Hydroxylated silica absorbs ∼1.6 monolayers of water under ambient conditions (296 K, ∼50% RH).; Using transmission FTIR, we monitored the reaction of surface-adsorbed HNO3 with gaseous CO, SO2, CH4 and NO. No reaction between HNO3 and CO, CH4 or SO2 was observed. Upper limits to the reaction probabilities (gammarxn ) were derived: ≤10-10 for CO and SO 2, and ≤10-12 for CH4. Therefore, these reactions are not expected to participate in "renoxification" in the boundary layer. However, the reaction of HNO3(ads) with NO does occur, producing gaseous NO2, with a lower limit for the reaction probability of gammaNO > (7 +/- 1) x 10-8 (2s) when only the surface area covered by HNO 3 was used. Molecular HNO3 was shown to be the reactive species instead of NO3-. This chemistry requires the presence of a thin water film on the surface. Recent studies by Kleffmann et al. (2004) reported to have an upper limit for the reaction probability for the HNO3-NO reaction of gamma NO→NO2 2.5 x 10-9. However, it is not clear whether the HNO3 was dissociated or the molecular form under their experimental conditions.; The HNO3-NO reaction could be a significant means of "renoxification" of HNO3 on surfaces. Therefore, the chemistry elucidated by these experiments may help to resolve some discrepancies between model-predicted ozone and field observations in polluted urban atmospheres.; The heterogeneous hydrolysis of NO2 under dark and light (400 ≤ gamma ≤ 500 nm) conditions, and pre-treating the silica surface with HNO3, as an important pathway for the production of HNO3(ads) was investigated. HNO3 remains surface-adsorbed, and hence available to further react with atmospheric species, such as NO. In the presence of light, the decay of HNO3(ads) was observed. Additionally, NO2 hydrolysis has been shown to slow down when occurring on acidified surfaces.
机译:目前观察到的磁场与模拟NOx / HNO3比之间的差异表明,可能影响大气氧化能力的化学物质仍未确定。我们研究了涉及HNO3和各种大气物质(NO,CO,CH4和SO2)的几种异构反应,这些反应旨在调和这些比率。确定了几个大气可用的自然和人为表面的BET表面积,以评估其在异质化学中的潜在作用。这些表面的BET表面积比样品的几何表面积高3至5个数量级。选择二氧化硅作为大气可利用表面的替代表面,并结合FTIR和BET理论研究了其与水的相互作用。羟基氧化硅在环境条件(296 K,约50%RH)下吸收约1.6单层水。使用透射式FTIR,我们监测了表面吸附的HNO3与气态CO,SO2,CH4和NO的反应。没有观察到HNO3与CO,CH4或SO2之间的反应。得出了反应概率的上限(gammarxn):CO和SO 2≤10-10,CH4≤10-12。因此,预期这些反应不会参与边界层中的“再氧化”。但是,HNO3(ads)与NO的确发生了反应,生成了气态NO2,只有当表面积覆盖在一定范围内时,γ的反应概率才会下限>(7 +/- 1)x 10-8(2s)。使用了HNO 3。分子HNO3被证明是反应性物质,而不是NO3-。这种化学作用要求表面上存在薄水膜。 Kleffmann等人的最新研究。 (2004年)报道说,对于伽马NO→NO2 <2.5 x 10-9的HNO3-NO反应,其反应概率具有上限。然而,尚不清楚HNO 3在其实验条件下是否解离或为分子形式。 HNO3-NO反应可能是HNO3在表面“重新氧化”的重要手段。因此,这些实验阐明的化学方法可能有助于解决模型预测的臭氧与污染的城市大气中的野外观测之间的某些差异。研究了在黑暗和明亮(400≤gamma≤500 nm)条件下NO2的非均相水解,并用HNO3预处理二氧化硅表面,将其作为生产HNO3(ads)的重要途径。 HNO3保持表面吸附,因此可用于与大气物质(例如NO)进一步反应。在光的存在下,观察到HNO 3(ads)的衰减。另外,已经证明当在酸化表面上发生时,NO 2水解减慢。

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