4 research outputs found
Variations and Sources of Organic Aerosol in Winter Beijing under Markedly Reduced Anthropogenic Activities During COVID-2019
The COVID-19 outbreak provides a
“controlled experiment”
to investigate the response of aerosol pollution to the reduction
of anthropogenic activities. Here we explore the chemical characteristics,
variations, and emission sources of organic aerosol (OA) based on
the observation of air pollutants and combination of aerosol mass
spectrometer (AMS) and positive matrix factorization (PMF) analysis
in Beijing in early 2020. By eliminating the impacts of atmospheric
boundary layer and the Spring Festival, we found that the lockdown
effectively reduced cooking-related OA (COA) but influenced fossil
fuel combustion OA (FFOA) very little. In contrast, both secondary
OA (SOA) and O3 formation was enhanced significantly after
lockdown: less-oxidized oxygenated OA (LO-OOA, 37% in OA) was probably
an aged product from fossil fuel and biomass burning emission with
aqueous chemistry being an important formation pathway, while more-oxidized
oxygenated OA (MO-OOA, 41% in OA) was affected by regional transport
of air pollutants and related with both aqueous and photochemical
processes. Combining FFOA and LO-OOA, more than 50% of OA pollution
was attributed to combustion activities during the whole observation
period. Our findings highlight that fossil fuel/biomass combustion
are still the largest sources of OA pollution, and only controlling
traffic and cooking emissions cannot efficiently eliminate the heavy
air pollution in winter Beijing
Contribution of Atmospheric Oxygenated Organic Compounds to Particle Growth in an Urban Environment
Gas-phase oxygenated organic molecules
(OOMs) can contribute substantially
to the growth of newly formed particles. However, the characteristics
of OOMs and their contributions to particle growth rate are not well
understood in urban areas, which have complex anthropogenic emissions
and atmospheric conditions. We performed long-term measurement of
gas-phase OOMs in urban Beijing during 2018–2019 using nitrate-based
chemical ionization mass spectrometry. OOM concentrations showed clear
seasonal variations, with the highest in the summer and the lowest
in the winter. Correspondingly, calculated particle growth rates due
to OOM condensation were highest in summer, followed by spring, autumn,
and winter. One prominent feature of OOMs in this urban environment
was a high fraction (∼75%) of nitrogen-containing OOMs. These
nitrogen-containing OOMs contributed only 50–60% of the total
growth rate led by OOM condensation, owing to their slightly higher
volatility than non-nitrate OOMs. By comparing the calculated condensation
growth rates and the observed particle growth rates, we showed that
sulfuric acid and its clusters are the main contributors to the growth
of sub-3 nm particles, with OOMs significantly promoting the growth
of 3–25 nm particles. In wintertime Beijing, however, there
are missing contributors to the growth of particles above 3 nm, which
remain to be further investigated
Insufficient Condensable Organic Vapors Lead to Slow Growth of New Particles in an Urban Environment
Atmospheric
new particle formation significantly affects global
climate and air quality after newly formed particles grow above ∼50
nm. In polluted urban atmospheres with 1–3 orders of magnitude
higher new particle formation rates than those in clean atmospheres,
particle growth rates are comparable or even lower for reasons that
were previously unclear. Here, we address the slow growth in urban
Beijing with advanced measurements of the size-resolved molecular
composition of nanoparticles using the thermal desorption chemical
ionization mass spectrometer and the gas precursors using the nitrate
CI-APi-ToF. A particle growth model combining condensational growth
and particle-phase acid–base chemistry was developed to explore
the growth mechanisms. The composition of 8–40 nm particles
during new particle formation events in urban Beijing is dominated
by organics (∼80%) and sulfate (∼13%), and the remainder
is from base compounds, nitrate, and chloride. With the increase in
particle sizes, the fraction of sulfate decreases, while that of the
slow-desorbed organics, organic acids, and nitrate increases. The
simulated size-resolved composition and growth rates are consistent
with the measured results in most cases, and they both indicate that
the condensational growth of organic vapors and H2SO4 is the major growth pathway and the particle-phase acid–base
reactions play a minor role. In comparison to the high concentrations
of gaseous sulfuric acid and amines that cause high formation rates,
the concentration of condensable organic vapors is comparably lower
under the high NOx levels, while those
of the relatively high-volatility nitrogen-containing oxidation products
are higher. The insufficient condensable organic vapors lead to slow
growth, which further causes low survival of the newly formed particles
in urban environments. Thus, the low growth rates, to some extent,
counteract the impact of the high formation rates on air quality and
global climate in urban environments
Molecular Composition of Oxygenated Organic Molecules and Their Contributions to Organic Aerosol in Beijing
The understanding at a molecular
level of ambient secondary organic
aerosol (SOA) formation is hampered by poorly constrained formation
mechanisms and insufficient analytical methods. Especially in developing
countries, SOA related haze is a great concern due to its significant
effects on climate and human health. We present simultaneous measurements
of gas-phase volatile organic compounds (VOCs), oxygenated organic
molecules (OOMs), and particle-phase SOA in Beijing. We show that
condensation of the measured OOMs explains 26–39% of the organic
aerosol mass growth, with the contribution of OOMs to SOA enhanced
during severe haze episodes. Our novel results provide a quantitative
molecular connection from anthropogenic emissions to condensable organic
oxidation product vapors, their concentration in particle-phase SOA,
and ultimately to haze formation
