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首页> 外文期刊>Journal of Geophysical Research, D. Atmospheres: JGR >Observational Constraints on the Formation of Cl_2 From the Reactive Uptake of ClNO_2 on Aerosols in the Polluted Marine Boundary Layer
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Observational Constraints on the Formation of Cl_2 From the Reactive Uptake of ClNO_2 on Aerosols in the Polluted Marine Boundary Layer

机译:从污染海洋边界层气溶胶中的CLNO_2反应性摄取的术后约束

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摘要

We use observations from the 2015 Wintertime Investigation of Transport, Emissions, and Reactivity (WINTER) aircraft campaign to constrain the proposed mechanism of Cl_2 production from ClNO_2 reaction in acidic particles. To reproduce Cl_2 concentrations observed during WINTER with a chemical box model that includes ClNO_2 reactive uptake to form Cl_2, the model required the ClNO_2 reaction probability, γ (ClNO_2), to range from 6 × 10~(-6) to 7 × 10~(-5), with a mean value of 2.3 × 10~(-5) (±1.8 × 10~(-5)). These field-determined γ (ClNO_2) are more than an order of magnitude lower than those determined in previous laboratory experiments on acidic surfaces, even when calculated particle pH is ≤2. We hypothesize this is because thick salt films in the laboratory enhanced the reactive uptake ClNO_2 compared to that which would occur in submicron aerosol particles. Using the reacto-diffusive length-scale framework, we show that the field and laboratory observations can be reconciled if the net aqueous-phase reaction rate constant for ClNO_2 (aq) + Cl~-(aq) in acidic particles is on the order of 10~4 s~(-1). We show that wet particle diameter and particulate chloride mass together explain 90% of the observed variance in the box model-derived γ (ClNO_2), implying that the availability of chloride and particle volume limit the efficiency of the reaction. Despite a much lower conversion of ClNO_2 into Cl_2, this mechanism can still be responsible for the nocturnal formation of 10-20 pptv of Cl_2 in polluted regions, yielding an atmospherically relevant concentration of Cl atoms the following morning.
机译:我们使用2015年冬季调查的运输,排放和反应性(冬季)飞机运动的观察,以限制Cl_2生产中的ClO_2在酸性颗粒中的反应中的提出机制。为了再现冬季观察到的CL_2浓度,用包括CLNO_2反应摄取的化学盒模型形成CL_2,所需的模型需要CLNO_2反应概率,γ(CLNO_2),范围为6×10〜(-6)至7×10〜 (-5),平均值为2.3×10〜(-5)(±1.8×10〜(-5))。这些现场确定的γ(CLNO_2)的数量级低于在酸性表面上的先前实验室实验中确定的阶数,即使当计算出的颗粒pH≤2时也是如此。我们假设这是因为实验室中的厚盐膜增强了反应性摄取ClNO_2,而与亚微米气溶胶颗粒中发生的相比。使用反应漫射长度框架,我们表明,如果酸性颗粒中的净水相反应速率常数为酸性颗粒的净水相反应速率常数,则可以和解场和实验室观察。 10〜4 s〜(-1)。我们表明,湿粒径和颗粒氯化物质量在一起解释了箱体模型衍生的γ(ClNO_2)中观察到的差异的90%,这意味着氯化物和粒子量的可用性限制了反应的效率。尽管ClNO_2转化为CL_2,但该机制仍然可以负责污染区中的CL_2的10-20 pptV的夜间形成,在第二天早晨产生了Cl原子的大气相关浓度。

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