Air quality is concerned with pollutants in both the gas phase and solid or liquid phases. The latter are referred to as aerosols, which are multifaceted agents affecting air quality, weather and climate through many mechanisms. Unlike gas pollutants, aerosols interact strongly with meteorological variables with the strongest interactions taking place in the planetary boundary layer (PBL). The PBL hosting the bulk of aerosols in the lower atmosphere is affected by aerosol radiative effects. Both aerosol scattering and absorption reduce the amount of solar radiation reaching the ground and thus reduce the sensible heat fluxes that drive the diurnal evolution of the PBL. Moreover, aerosols can increase atmospheric stability by inducing a temperature inversion as a result of both scattering and absorption of solar radiation, which suppresses dispersion of pollutants and leads to further increases in aerosol concentration in the lower PBL. Such positive feedback is especially strong during severe pollution events. Knowledge of the PBL is thus crucial for understanding the interactions between air pollution and meteorology. A key question is how the diurnal evolution of the PBL interacts with aerosols, especially in vertical directions, and affects air quality. We review the major advances in aerosol measurements, PBL processes and their interactions with each other through complex feedback mechanisms, and highlight the priorities for future studies.
Abstract. Cold frontal passages usually promote quick removal of atmospheric pollutants over
North China (e.g. the Beijing–Tianjin–Hebei region). However, in the Yangtze River
Delta (YRD), cold fronts may bring air pollutants from the polluted North China Plain
(NCP), thereby deteriorating the air quality in the YRD. In this study, a cold frontal
passage and a subsequent stable weather event over YRD during 21–26 January 2015 was
investigated with in situ observations and Weather Research and Forecasting – Community
Multiscale Air Quality Modeling System simulations. Observations showed a burst of
PM2.5 pollution and an obvious southward motion of PM2.5 peaks on the afternoon
of 21 January, suggesting a strong inflow of highly polluted air masses to YRD by a cold
frontal passage. Model simulations revealed an existing warm and polluted air mass over
YRD ahead of the frontal zone, which climbed to the free troposphere along the frontal
surface as the cold front passed, increasing the PM2.5 concentration at high
altitudes. Strong north-westerly frontal airflow transported particles from the highly
polluted NCP to the YRD. As the frontal zone moved downstream of YRD, high pressure took
control over the YRD, which resulted in a synoptic subsidence that trapped PM2.5 in
the boundary layer. After the cold frontal episode, a uniform pressure field took control
over the YRD. Locally emitted PM2.5 started to accumulate under the weak winds and
stable atmosphere. Tagging of PM2.5 by geophysical regions showed that the
PM2.5 contribution from the YRD itself was 35 % and the contribution from the
NCP was 29 % during the cold frontal passage. However, under the subsequent stable
weather conditions, the PM2.5 contribution from the YRD increased to 61.5 % and
the contribution from the NCP decreased to 14.5 %. The results of this study indicate
that cold fronts are potential carriers of atmospheric pollutants when there are strong
air pollutant sources in upstream areas, which may deteriorate air quality in downstream
regions.
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