Cooking organic aerosol (COA) is currently not included in European emission inventories. However, recent positive matrix factorization (PMF) analyses of aerosol mass
spectrometer (AMS) measurements have suggested important
contributions of COA in several European cities. In this
study, emissions of COA were estimated for the UK, based
on hourly AMS measurements of COA made at two sites in
London (a kerbside site in central London and an urban background site in a residential area close to central London) for the full calendar year of 2012 during the Clean Air for London (ClearfLo) campaign. Iteration of COA emissions estimates and subsequent evaluation and sensitivity experiments were conducted with the EMEP4UK atmospheric chemistry transport modelling system with a horizontal resolution of 5 km x 5 km.
The spatial distribution of these emissions was based on
workday population density derived from the 2011 census
data. The estimated UK annual COA emission was 7.4 Gg
per year, which is an almost 10% addition to the officially
reported UK national total anthropogenic emissions of PM2:5
(82 Gg in 2012), corresponding to 320 mgperson-1 day-1 on
average. Weekday and weekend diurnal variation in COA
emissions were also based on the AMS measurements. Modelled
concentrations of COA were then independently evaluated
against AMS-derived COA measurements from another
city and time period (Manchester, January–February 2007),
as well as with COA estimated by a chemical mass balance
model of measurements for a 2-week period at the Harwell
rural site (~80 km west of central London).
The modelled annual average contribution of COA to ambient
particulate matter (PM) in central London was between
1 and 2 μgm-3 (~20% of total measured OA1) and between
0.5 and 0.7 μgm-3 in other major cities in England
(Manchester, Birmingham, Leeds). It was also shown that
cities smaller than London can have a central hotspot of population density of smaller area than the computational grid cell, in which case higher localized COA concentrations than modelled here may be expected.
Modelled COA concentrations dropped rapidly outside of
major urban areas (annual average of 0.12 μgm-3 for the
Harwell location), indicating that although COA can be a notable component in urban air, it does not have a significant effect on PM concentrations on rural areas.
The possibility that the AMS-PMF apportionment measurements
overestimate COA concentrations by up to a factor
of 2 is discussed. Since COA is a primary emission, any
downward adjustments in COA emissions would lead to a proportional linear downward scaling in the absolute magnitudes of COA concentrations simulated in the model.