Miao Lei, Liao Xiao-Nong, Wang Ying-Chun
China Academy of Meteorological Science, Beijing 100081, China.
Institute of Urban Meteorology, China Meteorological Administration, Beijing 100089, China.
Huan Jing Ke Xue. 2016 Aug 8;37(8):2836-2846. doi: 10.13277/j.hjkx.2016.08.003.
Diurnal variation of PM mass concentration is analyzed based on data of BAOLIAN (representing urban area) and SAHNDIANZI BAP-Station (representing rural area) from 2005 to 2014. Furthermore, the influence of meteorological factors was also discussed. The results showed that 10-year-average diurnal variation of PM mass concentration in urban area had a two-peak pattern being coincident with rush-hour. However, it became clear only after 2007. The monthly (including seasonal) variation presented the change from one-peak pattern to two-peak pattern with the max mass concentration appearing in the morning or late afternoon during rush hour. The mass concentration in the morning rush hour reached its maximum between May and August which was to some degree related with weak wind and high relative humidity as well as great water vapor pressure (indicating the absolute water content in the air). But the smaller variety of mass concentration in the late afternoon attributed to the thicker mixing layer, higher wind speed and more showers. By contraries, it went up greatly after 4 pm in Nov., Dec., Jan. and Feb.. One of the reasons was that the height of mixing layer top decreased sharply. Besides, in some severely and seriously polluted days, the PM mass concentration increased after morning rush hour till afternoon which was different from the mean pattern and that in moderately polluted day. The main mechanism attributed to the aerosol from aerial source around brought by south wind to Beijing. The more severe the pollution was, the greater the daily concentration fluctuated. The range of PM diurnal variation was determined by the max wind speed and daily change of relative humidity in a day. Besides, it also extended the diurnal variation of concentration when the south wind speed reached 4-6 m·s in the afternoon. In rural area, the mean diurnal variation of PM mass concentration showed a one-peak pattern. And the time of concentration reaching its maximum was ahead of that of urban area. Moreover, the values in the day time during May and July were higher than that in winter. These results would be helpful to make policy for finer emission control when the atmosphere is in lower diffusivity situation.
基于2005年至2014年宝联(代表城市地区)和桑店子BAP站(代表农村地区)的数据,分析了颗粒物质量浓度的日变化。此外,还讨论了气象因素的影响。结果表明,城市地区颗粒物质量浓度的10年平均日变化呈双峰模式,与高峰时段一致。然而,这一模式直到2007年后才变得明显。月度(包括季节)变化呈现出从单峰模式到双峰模式的转变,最大质量浓度出现在高峰时段的早晨或傍晚。早晨高峰时段的质量浓度在5月至8月达到最大值,这在一定程度上与弱风、高相对湿度以及较大的水汽压(表示空气中的绝对含水量)有关。但傍晚质量浓度变化较小归因于混合层较厚、风速较高和阵雨较多。相反,在11月、12月、1月和2月,下午4点后质量浓度大幅上升。原因之一是混合层顶部高度急剧下降。此外,在一些重度和严重污染的日子里,颗粒物质量浓度在早晨高峰时段后直至下午都会增加,这与平均模式以及中度污染日不同。主要机制是南风将周边空中来源的气溶胶带到北京。污染越严重,日浓度波动越大。颗粒物日变化范围由一天中的最大风速和相对湿度的日变化决定。此外,当下午南风风速达到4 - 6米·秒时,也会延长浓度的日变化。在农村地区,颗粒物质量浓度的平均日变化呈单峰模式。浓度达到最大值的时间比城市地区提前。此外,5月和7月白天的值高于冬季。这些结果将有助于在大气扩散率较低的情况下制定更精细的排放控制政策。