TY - JOUR
T1 - Characteristics and source apportionment of PM 1 emissions at a roadside station
AU - Cheng, Y.
AU - Zou, S. C.
AU - Lee, S. C.
AU - Chow, J. C.
AU - Ho, K. F.
AU - Watson, J. G.
AU - Han, Y. M.
AU - Zhang, R. J.
AU - Zhang, F.
AU - Yau, P. S.
AU - Huang, Y.
AU - Bai, Y.
AU - Wu, W. J.
PY - 2011/11/15
Y1 - 2011/11/15
N2 - The mass concentrations of PM 1 (particles less than 1.0μm in aerodynamic diameter), organic carbon (OC), elemental carbon (EC), water-soluble ions, and up to 25 elements were reported for 24h aerosol samples collected every sixth day at a roadside sampling station in Hong Kong from October 2004 to September 2005. Annual average PM 1 mass concentration was 44.5±19.5μgm -3. EC, OM (organic matter, OC×1.2), and SO 4 = were the dominant components, accounting for ∼36%, ∼26%, and ∼24% of PM 1, respectively. Other components, i.e., NO 3 -, NH 4 +, geological material, trace elements and unidentified material, comprised the remaining ∼14%. Annual average OC/EC ratio (0.6±0.3) was low, indicating that primary vehicle exhaust was the major source of carbonaceous aerosols. The seasonal variations of pollutants were due to gas-particle partitioning processes or a change in air mass rather than secondary aerosol produced locally. Vehicle exhaust, secondary aerosols, and waste incinerator/biomass burning were dominant air pollution sources, accounting for ∼38%, ∼22% and ∼16% of PM 1, respectively. Pollution episodes during summer (May-August) which were frequently accompanied by tropical storms or typhoons were dominated by vehicle emissions. During winter (November-February) pollution episodes coincided with northeasterly monsoons were characterized by secondary aerosols and incinerator/biomass burning emissions.
AB - The mass concentrations of PM 1 (particles less than 1.0μm in aerodynamic diameter), organic carbon (OC), elemental carbon (EC), water-soluble ions, and up to 25 elements were reported for 24h aerosol samples collected every sixth day at a roadside sampling station in Hong Kong from October 2004 to September 2005. Annual average PM 1 mass concentration was 44.5±19.5μgm -3. EC, OM (organic matter, OC×1.2), and SO 4 = were the dominant components, accounting for ∼36%, ∼26%, and ∼24% of PM 1, respectively. Other components, i.e., NO 3 -, NH 4 +, geological material, trace elements and unidentified material, comprised the remaining ∼14%. Annual average OC/EC ratio (0.6±0.3) was low, indicating that primary vehicle exhaust was the major source of carbonaceous aerosols. The seasonal variations of pollutants were due to gas-particle partitioning processes or a change in air mass rather than secondary aerosol produced locally. Vehicle exhaust, secondary aerosols, and waste incinerator/biomass burning were dominant air pollution sources, accounting for ∼38%, ∼22% and ∼16% of PM 1, respectively. Pollution episodes during summer (May-August) which were frequently accompanied by tropical storms or typhoons were dominated by vehicle emissions. During winter (November-February) pollution episodes coincided with northeasterly monsoons were characterized by secondary aerosols and incinerator/biomass burning emissions.
KW - Chemical composition
KW - PM
KW - PMF
UR - https://www.scopus.com/pages/publications/80054105100
U2 - 10.1016/j.jhazmat.2011.08.005
DO - 10.1016/j.jhazmat.2011.08.005
M3 - 文章
C2 - 21907488
AN - SCOPUS:80054105100
SN - 0304-3894
VL - 195
SP - 82
EP - 91
JO - Journal of Hazardous Materials
JF - Journal of Hazardous Materials
ER -