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The European aerosol budget in 2006

机译:2006年欧洲气雾剂预算

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This paper presents the aerosol budget over Europe in 2006 calculated with the global transport model TM5 coupled to the size-resolved aerosol module M7. Comparison with ground observations indicates that the model reproduces the observed concentrations quite well with an expected slight underestimation of PM10 due to missing emissions (e.g. resuspension). We model that a little less than half of the anthropogenic aerosols emitted in Europe are exported and the rest is removed by deposition. The anthropogenic aerosols are removed mostly by rain (95%) and only 5% is removed by dry deposition. For the larger natural aerosols, especially sea salt, a larger fraction is removed by dry processes (sea salt: 70%, mineral dust: 35%). We model transport of aerosols in the jet stream in the higher atmosphere and an import of Sahara dust from the south at high altitudes. Comparison with optical measurements shows that the model reproduces the ?ngstr?m parameter very well, which indicates a correct simulation of the aerosol size distribution. However, we underestimate the aerosol optical depth. Because the surface concentrations are close to the observations, the shortage of aerosol in the model is probably at higher altitudes. We show that the discrepancies are mainly caused by an overestimation of wet-removal rates. To match the observations, the wet-removal rates have to be scaled down by a factor of about 5. In that case the modelled ground-level concentrations of sulphate and sea salt increase by 50% (which deteriorates the match), while other components stay roughly the same. Finally, it is shown that in particular events, improved fire emission estimates may significantly improve the ability of the model to simulate the aerosol optical depth. We stress that discrepancies in aerosol models can be adequately analysed if all models would provide (regional) aerosol budgets, as presented in the current study.
机译:本文介绍了2006年欧洲的气溶胶预算,其计算方法是将全球运输模型TM5与尺寸已解析的气溶胶模块M7结合使用。与地面观测值的比较表明,该模型可以很好地重现观测到的浓度,并且由于缺少排放(例如重悬)而导致PM10的预期轻微低估。我们的模型是,欧洲排放的不到一半的人为气溶胶是出口的,其余的则通过沉积去除。人为气溶胶主要通过雨水去除(95%),而仅5%通过干沉降去除。对于较大的天然气溶胶,尤其是海盐,则通过干法去除了较大的一部分(海盐:70%,矿物粉尘:35%)。我们模拟了高空大气中喷射流中气溶胶的运输,并模拟了高海拔地区从南部进口的撒哈拉尘埃。与光学测量结果的比较表明,该模型很好地再现了finstrm参数,这表明对气溶胶尺寸分布进行了正确的模拟。但是,我们低估了气溶胶的光学深度。由于表面浓度接近观测值,因此模型中气溶胶的短缺可能是在较高的高度。我们表明,差异主要是由于高估了除湿率。为了与观察结果相符,必须将除湿率降低约5倍。在这种情况下,模拟的地面硫酸盐和海盐浓度会增加50%(这会使匹配变差),而其他组件保持大致相同。最后,研究表明,在特定情况下,改进的火灾排放估算值可以显着提高模型模拟气溶胶光学深度的能力。我们强调,如本研究所述,如果所有模型都能提供(区域)气溶胶预算,则可以充分分析气溶胶模型中的差异。

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