Phillips, G.J.; Nemitz, E.
ORCID: https://orcid.org/0000-0002-1765-6298; Thomas, R.; Famulari, D.; Williams, P.; Allan, J.; Di Marco, C.
ORCID: https://orcid.org/0000-0002-9635-8191; Coe, H.; Harrison, R.M.; Fowler, D..
2009
Chemically-speciated aerosol fluxes above three UK cities.
[Speech]
In: European Aerosol Conference, Karlsruhe, 6-11 Sept 2009.
Karlsruhe, Germany, T130A02.
Abstract
There is considerable uncertainty regarding
the processes controlling the formation and
transformation of organic aerosol (OA) in the
atmosphere. Regional aerosol, advected into the city,
mixes with the primary urban emissions of particles
and VOCs to create an environment where particle
composition is controlled by a number of factors, not
least chemistry and complex urban meteorology.
Measurements of chemically-speciated particle
fluxes above urban areas can give us insight into
exchanges between urban centres and the free
troposphere, as well as the chemical and physical
processing which occurs during transport.
We present chemically-speciated aerosol
fluxes and concentrations measured three contrasting
cities in the United Kingdom. An aerodyne
quadropole-AMS was deployed on a tall building in
the three urban centers; the Nelson Monument in
Edinburgh, the Portland Tower in Manchester and
the BT Tower in London. We use the coupled eddy
covariance-AMS system as described in Nemitz et
al., 2008 to measure the flux of non-refractory (NR)
PM1 above the three cities. Supporting
measurements of CO and CO2 fluxes made by eddy
covariance are also presented and emission factors
relative to these pollution tracers have been
calculated.
The organic aerosol component of the NRPM1
mass has been further analysed using statistical
techniques to ascertain the contribution to the OA
flux and concentration of so-called hydrocarbon-like
organic aerosol (HOA) and oxygenated organic
aerosol (OOA). OA dominates the mass of PM1 in
all three cities with nitrate the next major component
of the mass in Edinburgh and Manchester and sulfate
the next major component in London. HOA
dominates the OA mass in Edinburgh and for some
time periods in Manchester, in contrast to the finding
of Zhang et al., for urban areas and situation in
London where OOA was the larger proportion of the
OA mass.
At all locations, HOA has a large relative
emission flux relative to OOA. The HOA fluxes are
generally are generally upward and show diurnal
trend. Average flux densities of hydrocarbon-like
organic aerosol (HOA) range from 63 ng m-2 s-1 in
Edinburgh to 440 ng m-2 s-1 in London. Excellentcorrelation was found between emission fluxes of CO
and CO2. However, HOA fluxes show a much
weaker correlation with these gases. Changes in the
relative emission strengths of HOA and CO2 are
likely related to changes in the fuel mix, vehicle fleet
and the changing contribution of building heating.
However, the relatively constant CO/CO2 flux ratio
suggests that i) these changes were not pronounced
and ii) was without a significant biogenic component;
implying the CO2 emission flux was due mainly to
combustion. Assuming that both HOA and CO2 (and
CO) originate from similar sources, the
measurements suggest that HOA undergoes
considerable processing between emission and
measurement of the flux high above the urban centre.
The fraction of HOA that is evaporated and/or
chemically processed is likely to depend on
measurement height, temperature, radiation,
photochemistry, and transport time-scale.
Nevertheless, as the transport time-scale during these
measurements is on the order of minutes to tens of
minutes, the flux ratio HOA/CO2 is likely to be more
representative than emission ratios derived from
urban concentration ratios, which accumulate over
tens of minutes to hours. Emission ratios range from
0.24 to 1.37 g (kg C)-1.
The authors thank BT, Edinburgh City
Council and Bruntwood for logistical support and
access to the field sites. This work was funded by the
NERC CityFlux project and the BT tower
deployment was also part of the REPARTEE
experiment described by Harrison et al. in this
session.
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