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HAZE-TO-FOG TRANSFORMATION DURING A LONG LASTING, LOW VISIBILITY EPISODE IN NANJING

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doi: 10.16555/j.1006-8775.2016.S1.007

  • Haze-to-fog transformation during a long lasting, low visibility episode was examined using the observations from a comprehensive field campaign conducted in Nanjing, China during 4-9 December 2013. In this episode, haze was transformed into fog and the fog lasted for dozens of hours. The impacts of meteorological factors such as wind, temperature (T) and relative humidity (RH) on haze, transition and fog during this episode were investigated. Results revealed significant differences between haze and fog days, due to their different formation mechanisms. Comparison was made for boundary-layer conditions during hazy days, haze-to-fog days and foggy days. Distributions of wind speed and wind direction as well as synoptic weather conditions around Nanjing had determinative impacts on the occurrences and characteristics of haze and fog. Weakened southerly wind in southern Nanjing resulted in high concentration of pollutants, and haze events occurred frequently during the study period. The wind speed was less than 1 m s-1 in the haze event, which resulted in a stable atmospheric condition and weak dispersion of the pollutants. The height of the temperature inversion was about 400 m during the period. The inversion intensity was weak and the temperature-difference was 4°C km-1 or less in haze, while the inversion was stronger, and temperature-difference was about 6°C km-1, approaching the inversion layer intensity in the fog event. Haze event is strongly influenced by ambient RH. RH values increased, which resulted in haze days evidently increased, suggesting that an increasing fraction of haze events be caused by hygroscopic growth of aerosols, rather than simply by high aerosol loading. When RH was above 90%, haze aerosols started to be transformed from haze to fog. This study calls for more efforts to control emissions to prevent haze events in the region.
  • [1] JACQUELINE D C, ANDREW J G, JAMES M S, et al. Cytokine production by human airway epithelial cells after exposure to an air pollution particle is metal-dependent [J]. Toxicol Appl Pharmac, 1997, 146(1997): 180-188.
    [2] POSCHL U. Atmospheric aerosols: composition, transformation, climate and health effects [J]. Agenwandte Chemie Int Ed, 2005, 44(46): 7 520-7 540.
    [3] TIE Xue-xi, BRASSEUR G P, ZHAO Chun-sheng, et al. Chemical characterization of air pollution in Eastern China and the Eastern United States [J]. Atmos Environ, 2006, 40: 2 607-2 625.
    [4] FU Qing-yan, ZHUANG Guo-shun, WANG Jing, et al. Mechanism of formation of the heaviest pollution episode ever recorded in the Yangtze River Delta, China [J]. Atmos Environ, 2008, 42: 2 023-2 036.
    [5] CHEN J, ZHAO C S, MA N, et al. A parameterization of low visibilities for hazy days in the North China Plain [J]. Atmos Chem Phys, 2012, 12: 4 935-4 950.
    [6] FAN S X, HUANG H L, FAN T, et al. Size distribution characteristics of polycyclic aromatic hydrocarbons of PM10 in foggy days in the north suburb of Nanjing [J]. Environ Sci, 2009, 30(9): 2 707-2 715.
    [7] OKADA K M, IKEGAMI, ZAIZEN Y. The mixture state of individual aerosol particles in the 1997 Indonesian haze episode [J]. J Aerosol Sci, 2001, 32(11): 1 269-1 279.
    [8] HE Jia-bao, FAN Shu-xian, MENG Qing-zi, et al. Polycyclic aromatic hydrocarbons (PAHs) associated with fine particulate matters in Nanjing, China: Distributions, sources and meteorological influences [J]. Atmos Environ, 2014, 89(2014): 207-215.
    [9] LAI L Y, SEQUEIRA Y R. Visibility degradation across Hong Kong: its components and their relative contributions [J]. Atmos Environ, 2001, 35(34): 5 861-5 872.
    [10] LI Z Q, Gu X, WANG L, et al. Aerosol physical and chemical properties retrieved from ground-based remote sensing measurements during heavy haze days in Beijing winter [J]. Atmos Chem Phys Discuss, 2013, 13(2): 5 091-5 122.
    [11] PILIE R J, MACK E J, KOCMOND W C, et al. The life cycle of valley fog. Part I: Micrometeorological characteristics [J]. J Appl Meteorol, 1975, 14(1975): 347-364.
    [12] ROACH W T, BROWN R, CAUGHEY S J, et al. Readings. The physics of radiation fog: I- a field study [J]. Quart J Roy Meteorol Soc, 1976, 102: 313-333.
    [13] WANG Hong-lei, AN Jun-lin, SHEN Li-juan, et al. Mechanism for the formation and microphysical characteristics of submicron aerosol during heavy haze pollution episode in the Yangtze River Delta, China [J]. Sci Total Environ, 2014, 490(2014): 501-508.
    [14] CHANG Di, SONG Yu, and LIU Bing. Visibility trends in six megacities in China 1973-2007 [J]. Atmos Res, 2009, 94: 161-167.
    [15] CHAN C K, Yao Xiaohong. Air pollution in mega cities in China [J]. Atmos Environ, 2008, 42(1): 1-42.
    [16] CHEN Xun-lai, FENG Ye-rong, WANG An-yu, et al. Numerical experiment research on air pollutants during atmospheric haze over the multi-cities of Pearl River Delta region [J]. Acta Sci Nat Univ Sunyatseni, 2007, 46(4): 103-107 (in Chinese).
    [17] CHEN Y, ZHAO C, ZHANG Q, et al. Aircraft study of mountain chimney effect of Beijing, China [J]. J Geophys Res, 2009, 114: D08306.
    [18] DAI Yong-li, TAO Jun, LIN Ze-jian, et al. Characteristics of haze and its impact factors in four megacities in China during 2006-2009 [J]. Environ Sci, 2013, 34(8): 2 925-2 933.
    [19] JIA Xing-can, GUO Xue-liang. Impacts of anthropogenic atmospheric pollutant on formation and development of a winter heavy fog event [J]. China J Atmos Sci, 2012, 36: 995-1 008 (in Chinese).
    [20] GAUTAM R, HSU N C, KAFATOS M, et al. Influences of winter haze on fog/low cloud over the Indo-Gangetic [J]. J Geophys Res, 2007, 112: 207-218.
    [21] LU Chun-song, NIU Sheng-jie, TANG Li-li, et al. Chemical composition of fog water in Nanjing area of China and its related fog microphysics [J]. Atmos Res, 2010, 97(2010): 47-69.
    [22] ROBERTS G C, NENES A. A continuous-flow streamwise thermal-gradient CCN chamber for atmospheric measurements [J]. Aerosol Sci Tech, 2005, 39: 206-221.
    [23] LANCE S, SMITH J, NENES A. Mapping the operation of the DMT continuous flow CCN counter [J]. Aerosol Sci Tech, 2006, 40: 242-254.
    [24] LI Li, YIN Yan, GU Xue-song, et al. Observational study of cloud condensation nuclei properties at various altitudes of Huangshan Mountains [J]. Chin J Atmos Sci, 2014, 38(3): 410-420.
    [25] TARDIF R, RASMUSSEN R M. Event-based climatology and typology of fog in the New York city region [J]. J Appl Meteor Climatol, 2007, 46: 1 141-1 168.
    [26] ELIAS T, HAEFFELIN M, DROBINSKI P, et al. Particulate contribution to extinction of visible radiation: Pollution, haze, and fog [J]. Atmos Res, 2009, 92: 443-454.
    [27] YANG Xin, CHEN Yi-zhen, LIU Hou-feng, et al. Characteristics and formation mechanism of a winter haze-fog episode in Tianjin, China [J]. Atmos Environ 2014, 98(2014): 323-330.
    [28] DENG Z Z, ZHAO C S, MA N, et al. An examination of parameterizations for the CCN number concentration based on in situ measurements of aerosol activation properties in the North China Plain [J]. Atmos Chem Phys, 2013, 13: 6 227-6 237.
    [29] ZHANG J K, SUN Y, LIU Z R, et al. Characterization of submicron aerosols during a serious pollution month in Beijing (2013) using an aerodyne high-resolution aerosol mass spectrometer [J]. Atmos Chem Phys Discuss, 2013, 13(7): 19 009-19 049.
    [30] PETER K K, JOHN G W, JUDITH C C, et al. Aleis. Seasonal characteristics and regional transport of PM2.5 in Hong Kong [J]. Atoms Environ, 2005, 39(2005): 1 695-1 710.
    [31] XU Feng, NIU Sheng-jie, ZHANG Yu, et al. Analyses on chemical characteristic of spring sea fog water on Donghai Island in Zhanjiang, China [J]. China Environ Sci, 2011, 31(3): 353-360.
    [32] GAO Jian, WANG Tao, ZHOU Xue-hua, et al. Measurement of aerosol number size distributions in the Yangtze River delta in China: formation and growth of particles under polluted conditions [J]. Atmos Environ, 2009, 43: 829-836.
    [33] NIU Sheng-jie, LU Chun-song, Yu Hua-ying, et al. Fog research in China: an overview [J]. Adv Atmos Sci, 2010, 27(3): 639-662.
    [34] HUSAR R B, HOLLOWAY J M. The properties and climate of atmospheric haze [J]. Hygroscopic Aerosols, Hampton Virginia, A Deepak Publishing. 1984: 129-170.

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ZHANG Shu-ting, NIU Sheng-jie. HAZE-TO-FOG TRANSFORMATION DURING A LONG LASTING, LOW VISIBILITY EPISODE IN NANJING [J]. Journal of Tropical Meteorology, 2016, 22(S1): 67-77, https://doi.org/10.16555/j.1006-8775.2016.S1.007
ZHANG Shu-ting, NIU Sheng-jie. HAZE-TO-FOG TRANSFORMATION DURING A LONG LASTING, LOW VISIBILITY EPISODE IN NANJING [J]. Journal of Tropical Meteorology, 2016, 22(S1): 67-77, https://doi.org/10.16555/j.1006-8775.2016.S1.007
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Manuscript revised: 15 March 2016
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HAZE-TO-FOG TRANSFORMATION DURING A LONG LASTING, LOW VISIBILITY EPISODE IN NANJING

doi: 10.16555/j.1006-8775.2016.S1.007

Abstract: Haze-to-fog transformation during a long lasting, low visibility episode was examined using the observations from a comprehensive field campaign conducted in Nanjing, China during 4-9 December 2013. In this episode, haze was transformed into fog and the fog lasted for dozens of hours. The impacts of meteorological factors such as wind, temperature (T) and relative humidity (RH) on haze, transition and fog during this episode were investigated. Results revealed significant differences between haze and fog days, due to their different formation mechanisms. Comparison was made for boundary-layer conditions during hazy days, haze-to-fog days and foggy days. Distributions of wind speed and wind direction as well as synoptic weather conditions around Nanjing had determinative impacts on the occurrences and characteristics of haze and fog. Weakened southerly wind in southern Nanjing resulted in high concentration of pollutants, and haze events occurred frequently during the study period. The wind speed was less than 1 m s-1 in the haze event, which resulted in a stable atmospheric condition and weak dispersion of the pollutants. The height of the temperature inversion was about 400 m during the period. The inversion intensity was weak and the temperature-difference was 4°C km-1 or less in haze, while the inversion was stronger, and temperature-difference was about 6°C km-1, approaching the inversion layer intensity in the fog event. Haze event is strongly influenced by ambient RH. RH values increased, which resulted in haze days evidently increased, suggesting that an increasing fraction of haze events be caused by hygroscopic growth of aerosols, rather than simply by high aerosol loading. When RH was above 90%, haze aerosols started to be transformed from haze to fog. This study calls for more efforts to control emissions to prevent haze events in the region.

ZHANG Shu-ting, NIU Sheng-jie. HAZE-TO-FOG TRANSFORMATION DURING A LONG LASTING, LOW VISIBILITY EPISODE IN NANJING [J]. Journal of Tropical Meteorology, 2016, 22(S1): 67-77, https://doi.org/10.16555/j.1006-8775.2016.S1.007
Citation: ZHANG Shu-ting, NIU Sheng-jie. HAZE-TO-FOG TRANSFORMATION DURING A LONG LASTING, LOW VISIBILITY EPISODE IN NANJING [J]. Journal of Tropical Meteorology, 2016, 22(S1): 67-77, https://doi.org/10.16555/j.1006-8775.2016.S1.007
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