Abstract. Atmospheric aerosols are a significant public health hazard and have
substantial impacts on the climate. Secondary organic aerosols (SOAs) have
been shown to phase separate into a highly viscous organic outer layer
surrounding an aqueous core. This phase separation can decrease the
partitioning of semi-volatile and low-volatile species to the organic phase
and alter the extent of acid-catalyzed reactions in the aqueous core. A new
algorithm that can determine SOA phase separation based on their glass
transition temperature (Tg), oxygen to carbon (O:C) ratio and organic mass
to sulfate ratio, and meteorological conditions was implemented into the
Community Multiscale Air Quality Modeling (CMAQ) system version 5.2.1 and
was used to simulate the conditions in the continental United States for the
summer of 2013. SOA formed at the ground/surface level was predicted to be
phase separated with core–shell morphology, i.e., aqueous inorganic core
surrounded by organic coating 65.4 % of the time during the 2013 Southern
Oxidant and Aerosol Study (SOAS) on average in the isoprene-rich southeastern
United States. Our estimate is in proximity to the previously reported
∼70 % in literature. The phase states of organic coatings
switched between semi-solid and liquid states, depending on the
environmental conditions. The semi-solid shell occurring with lower aerosol
liquid water content (western United States and at higher altitudes) has a
viscosity that was predicted to be 102–1012 Pa s, which
resulted in organic mass being decreased due to diffusion limitation.
Organic aerosol was primarily liquid where aerosol liquid water was dominant
(eastern United States and at the surface), with a viscosity <102 Pa s.
Phase separation while in a liquid phase state, i.e.,
liquid–liquid phase separation (LLPS), also reduces reactive uptake rates
relative to homogeneous internally mixed liquid morphology but was lower
than aerosols with a thick viscous organic shell. The sensitivity cases
performed with different phase-separation parameterization and dissolution
rate of isoprene epoxydiol (IEPOX) into the particle phase in CMAQ can have
varying impact on fine particulate matter (PM2.5) organic mass, in
terms of bias and error compared to field data collected during the 2013 SOAS.
This highlights the need to better constrain the parameters that
govern phase state and morphology of SOA, as well as expand mechanistic
representation of multiphase chemistry for non-IEPOX SOA formation in models
aided by novel experimental insights.