Fan Shu-Xian, Huang Hong-Li, Fan Tao, Tang Li-Li, Yang Xue-Zhen, Li Hong-Shuang
Key Laboratory of Meteorological Disaster of Ministry of Education, Nanjing University of Information Science & Technology, Nanjing 210044, China.
Huan Jing Ke Xue. 2009 Sep 15;30(9):2707-14.
Based on meteorological data and aerosol samples from Nov.15 to Dec.30,2007 in the north suburb of Nanjing, size distribution characteristics of polycyclic aromatic hydrocarbons (PAHs) in PM10 in foggy and sunny days were studied, and the concentrations of 16 PAHs were analyzed by gas chromatography with mass selective detection (GC-MS). The average concentrations of aerosols in the night (PM2.1 : 120.34 microg x m(-3; PM10 : 215.92 microg*m(-3) are close to those in the daytime (PM2.1 : 26.76 microg.m(-3); PM9.0 : 213.41 microg x m(-3)) in foggy days. The average concentrations of aerosols are higher in the night (PM2.1 : 71.45 microg x m(-3); PM9.0 : 114.33 microg x m(-3)) than those in the daytime (PM2.1 : 41.02 microg x m(-3); PM9.0 : 74.38 microg x m(-3)) in fine days. And we also find that the total concentrations of 16 PAHs in PM2.1 (49.97 ng x m(-3)) and PM9.0 (59.45 ng x m(-3)) in foggy days are 1.50 and 1.46 times of those (PM2.1 : 33.30 ng x m(-3); PM9.0 : 40.80 ng x m(-3)) in fine days separately. The average maximum concentrations of individual PAHs are fluoranthene, which are higher (PM2.1 : 7.98 ng x m(-3); PM9.0 : 9.99 ng x m(-3)) in foggy days than those (PM2.5 : 5.23 ng x m(-3); PM9.0 : 6.77 ng x m(-3)) in fine days, and the average concentrations of benzo-apyrene are higher in fog days (PM2.1 : 1.77 ng x m(-3); PM9.0 : 1.99 ng x m(-3)) than those in fine days (PM2.1 : 1.46 microg x m(-3); PM9.0 : 1.84 ng x m(-3)).Those results indicate that the fog processing could aggravate the pollution of PM2.5 and PM10 near the ground layer. Diurnal size distribution of total PAHs in PM10 is consistent with that of PM10 in foggy and sunny days, and size distribution investigated was bi-modal with a peak in accumulation particle mode and another peak in coarse particle mode aerosol. Size distributions of PM10 and total PAHs in PM10 are affected greatly by the day fog in daytime, while those are affected little by the night fog in night.
基于2007年11月15日至12月30日南京北郊的气象数据和气溶胶样本,研究了雾天和晴天时PM10中多环芳烃(PAHs)的粒径分布特征,并用气相色谱 - 质谱选择性检测法(GC - MS)分析了16种PAHs的浓度。雾天夜间气溶胶的平均浓度(PM2.1:120.34μg·m⁻³;PM10:215.92μg·m⁻³)与白天(PM2.1:26.76μg·m⁻³;PM9.0:213.41μg·m⁻³)接近。晴天时,夜间气溶胶的平均浓度(PM2.1:71.45μg·m⁻³;PM9.0:114.33μg·m⁻³)高于白天(PM2.1:41.02μg·m⁻³;PM9.0:74.38μg·m⁻³)。此外,我们还发现,雾天PM2.1(49.97ng·m⁻³)和PM9.0(59.45ng·m⁻³)中16种PAHs的总浓度分别是晴天时(PM2.1:33.30ng·m⁻³;PM9.0:40.80ng·m⁻³)的1.50倍和1.46倍。单个PAHs的平均最大浓度为荧蒽,雾天(PM2.1:7.98ng·m⁻³;PM9.0:9.99ng·m⁻³)中的浓度高于晴天(PM2.5:5.23ng·m⁻³;PM9.0:6.77ng·m⁻³),雾天中苯并[a]芘的平均浓度(PM2.1:1.77ng·m⁻³;PM9.0:1.99ng·m⁻³)高于晴天(PM2.1:1.46μg·m⁻³;PM9.0:1.84ng·m⁻³)。这些结果表明,雾的作用会加重近地层PM2.5和PM10的污染。PM10中总PAHs的日粒径分布与雾天和晴天时PM10的粒径分布一致,所研究的粒径分布为双峰型,在积聚颗粒模态和粗颗粒模态气溶胶中各有一个峰值。白天的雾对PM10及其总PAHs的粒径分布影响较大,而夜间的雾影响较小。