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应用SMPS (Scanning Mobility Particle Sizer)对ETS (Environmental Tobacco Smoke)亚微米颗粒物的粒径谱演变进行了测量分析.结果发现,ETS颗粒物在10~500nm范围内呈对数正态单峰分布,数量粒径谱和质量粒径谱的演化有类似的递减趋势,但其浓度衰减率有明显的不同.分析得知,由于在演化过程中颗粒物直径是动态变化的,并不能用简单的方法获得凝并和沉积损失率.

参考文献

[1] Jones AP .Indoor air quality and health[J].Atmospheric environment,1999(28):4535-4564.
[2] Lambert W E;Samet J M;Spengler J D .Environmental Tobacco Smoke Concentrations in No-Smoking and Smoking Sections of Restaurants[J].American Journal of Public Health,1993,83(09):1339-1341.
[3] Morawska L.;Bofinger ND.;Jamriska M. .SIZE CHARACTERISTICS AND AGEING OF THE ENVIRONMENTAL TOBACCO SMOKE[J].Science of the Total Environment,1997(1):43-55.
[4] Hinds W C.Aerosol Technology:Properties,Behavior,and Measurement of Airborne Particles[M].New York:John Wiley and Sons,Inc,1982
[5] 孙在,黄震,王嘉松.亚微米颗粒物的沉积与凝并的模拟与实验研究[J].上海交通大学学报,2007(10):1710-1713.
[6] William Nazaroff .Indoor particle dynamics[J].Indoor air,2004(7):175-183.
[7] Jamriska M;Morawska L .Quantitative Assessment of the Effect of Surface Deposition and Coagulation on the Dynamies of Submicrometer Particle Indoors[J].Aerospace Science and Technology,2003,37:425-436.
[8] Neil E.Klepeis;Michael G.Apte;Lara A.Gundel;Richard G.Sextro;William W.Nazaroff .Determining size-specific emission factors for environmental tobacco smoke particles[J].Aerosol Science and Technology: The Journal of the American Association for Aerosol Research,2003(10):780-790.
[9] Sun Zai;Huang Zhen;Wang Jia-song .Studies on the size distribution,number and mass emission factors of candle particles characterized by modes of burning[J].Journal of Aerosol Science,2006(11):1484-1496.
[10] D.S. Kim;S.H.Park;Y.M.Song;D.H.Kim;K.W.Lee .Brownian coagulation of polydisperse aerosols in the transition regime[J].Journal of Aerosol Science,2003(7):859-868.
[11] Xu M;Nematollahi M;Sextro R G et al.Deposition of Tobacco Smoke Particles in a Low Ventilation Room[J].Aerospace Science and Technology,1994,20:194-206.
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