Abstract

Abstract. In January 2013, North China Plain experienced several serious haze events. Cimel sunphotometer measurements at seven sites over rural, suburban and urban regions of North China Plain from 1 to 30 January 2013 were used to further our understanding of spatial-temporal variation of aerosol optical parameters and aerosol radiative forcing (ARF). It was found that Aerosol Optical Depth at 500 nm (AOD500 nm) during non-pollution periods at all stations was lower than 0.30 and increased significantly to greater than 1.00 as pollution events developed. The Angstrom exponent (Alpha) was larger than 0.80 for all stations most of the time. AOD500 nm averages increased from north to south during both polluted and non-polluted periods on the three urban sites in Beijing. The fine mode AOD during pollution periods is about a factor of 2.5 times larger than that during the non-pollution period at urban sites but a factor of 5.0 at suburban and rural sites. The fine mode fraction of AOD675 nm was higher than 80% for all sites during January 2013. The absorption AOD675 nm at rural sites was only about 0.01 during pollution periods, while ~0.03–0.07 and 0.01–0.03 during pollution and non-pollution periods at other sites, respectively. Single scattering albedo varied between 0.87 and 0.95 during January 2013 over North China Plain. The size distribution showed an obvious tri-peak pattern during the most serious period. The fine mode effective radius in the pollution period was about 0.01–0.08 μm larger than during non-pollution periods, while the coarse mode radius in pollution periods was about 0.06–0.38 μm less than that during non-pollution periods. The total, fine and coarse mode particle volumes varied by about 0.06–0.34 μm3, 0.03–0.23 μm3, and 0.03–0.10 μm3, respectively, throughout January 2013. During the most intense period (1–16 January), ARF at the surface exceeded −50 W m−2, −180 W m−2, and −200 W m−2 at rural, suburban, and urban sites, respectively. The ARF readings at the top of the atmosphere were approximately −30 W m−2 in rural and −40–60 W m−2 in urban areas. Positive ARF at the top of the atmosphere at the Huimin suburban site was found to be different from others as a result of the high surface albedo due to snow cover.

Highlights

  • Aerosol particles can result in direct radiative forcing and they have indirect effects on clouds (Hansen et al, 1997)

  • The AOD at urban, suburban, and rural stations shows consistent variations during the pollution month in 2013, which indicates that serious pollution not a local but a regional phenomenon in North China Plain

  • The fine mode AOD during the pollution period at urban sites is about a factor of 2.5 compared with the non-pollution period, and a factor of ∼ 5 times the values in the suburban and rural sites

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Summary

Introduction

Aerosol particles can result in direct radiative forcing and they have indirect effects on clouds (Hansen et al, 1997). There are several well-known ground-based aerosol-monitoring networks that use sunphotometers such as the Aerosol Robotic Network-AERONET (Holben et al, 1998), PHOtométrie pour le Traitement Opérationnel de Normalisation Satellitaire (PHOTONS) (Goloub et al, 2008), AEROCAN (Bokoye et al, 2001), China Aerosol Remote Sensing Network (CARSNET) (Che et al, 2009a), and SKYNET network (Takamura and Nakajima, 2004) These networks have been used to measure direct and diffuse solar radiation and derived aerosol optical properties for the purpose of aerosol radiative forcing studies (Dubovik et al, 2002; Kim et al, 2004). These researches will help to uncover the regional climate effect of aerosol particles and the mechanism of pollution event formation, and will allow managers to control air quality better in the future

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