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高空偏北风背景下北京地区高污染形成的环境气象机制研究
摘要点击 3435  全文点击 1685  投稿时间:2014-09-09  修订日期:2014-11-03
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中文关键词  高空偏北气流  高污染  动力作用  下沉气流层  低层辐合  风速脉动
英文关键词  northerly flow at upper levels  serious air pollution event  dynamic effect  downdraft layer  underlying convergence  wind speed pulses
作者单位E-mail
廖晓农 中国气象局北京城市气象研究所, 北京 100089
中国气象局京津冀环境气象预报预警中心, 北京 100089 
cristinlxn@126.com 
孙兆彬 中国气象局京津冀环境气象预报预警中心, 北京 100089  
唐宜西 中国气象局京津冀环境气象预报预警中心, 北京 100089  
蒲维维 中国气象局京津冀环境气象预报预警中心, 北京 100089  
李梓铭 中国气象局京津冀环境气象预报预警中心, 北京 100089  
卢冰 中国气象局北京城市气象研究所, 北京 100089  
中文摘要
      在北京地区,有一类高污染产生在850 hPa以上为偏北风的背景下.利用气象观测资料、NCEP再分析资料和地面PM2. 5浓度监测结果分析了环境气象条件在这类污染过程形成中的作用.结果表明,在污染物浓度逐渐升高的过程中,环境大气并不总是处在层结稳定状态,有利于污染物累积的气象条件来自垂直运动和散度在垂直方向上的"分层"结构.从地面到对流层中层,垂直速度呈上升-下沉-上升的分布,而且散度呈辐合-辐散-辐合的结构.近地层的辐合导致周边的污染物向本地汇集,上升运动则将它们送向空中.但是,叠置在其上空的、长时间维持的下沉气流层却阻止了污染物继续向上运动,从而导致近地面层的污染浓度不断升高.垂直运动出现"分层"是由于高空偏北风并没有侵入到边界层内,近地层仍然维持偏南风或小风,冷空气太弱或者没有冷空气活动是高空偏北风不能到达近地层的主要原因.而下沉气流层的形成则与其上空的空气辐合有关,该辐合层源自偏北气流中的风速脉动.因此,环境大气动力作用是高空偏北气流型空气污染过程形成的关键机制.关注对流层中下层温度24 h变化、垂直速度和散度的垂直分布将有助于提高此类高污染过程的诊断分析和预报能力.
英文摘要
      There is a kind of serious air pollution case occurring in the situation of northerly flow at the levels above 850 hPa in Beijing area. Meteorological data, NCEP reanalysis data and PM2.5 concentration survey were used to analyze the roles of meteorological mechanism in this kind of air pollution case. The results showed that the stable stratification did not exist all the time during the gradual increase of PM2.5 concentration. The favorable meteorological conditions in PM2.5 accumulation came from the layered structure of vertical speed and convergence in vertical direction. From the surface to the middle level of troposphere, the vertical velocity showed an updraft-downdraft-updraft distribution. And the divergence displayed a convergence-divergence-convergence structure. The convergence at lower levels led to the gathering of the polluted air from the surrounding and the ascending current brought it upwards. However, the polluted air could not go further up due to the prolonged downdraft layer above. As the result, PM2.5 near the surface was concentrated gradually. The vertical speed in layer structure was attributed to the high level northerly flow without invading into the boundary layer. In such case, the wind was still in southerly direction or kept calm at the surface. The weak cold air or no cold air at all was the main reason that the northerly flow could not hit the surface. The developed downdraft layer was relative to the convergence above which was resulted from the wind speed pulses in the northerly flow at upper levels. In conclusion, the air dynamical effect played a key role in the pollution type of northerly flow at upper levels. Therefore, it will be beneficial to enhance our capability in the analysis and forecasting of this kind of pollution case by focusing on 24 hours temperature variation at the middle and lower troposphere as well as the vertical distribution of vertical velocity and divergence.

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