Air quality expert group - Fine particulate matter (PM2.5) in ... - Defra
Air quality expert group - Fine particulate matter (PM2.5) in ... - Defra
Air quality expert group - Fine particulate matter (PM2.5) in ... - Defra
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Modell<strong>in</strong>g <strong>PM2.5</strong> and the future<br />
wide range of applications related to predict<strong>in</strong>g and understand<strong>in</strong>g <strong>PM2.5</strong>.<br />
These applications <strong>in</strong>clude work to better quantify the non-l<strong>in</strong>earities of <strong>PM2.5</strong><br />
formation <strong>in</strong> response to precursor emission reductions, the prediction of the<br />
<strong>in</strong>dividual components that contribute to <strong>PM2.5</strong> mass, short-term forecast<strong>in</strong>g<br />
and the longer term prediction of trends, and how predictions compare with<br />
measured values.<br />
11. The CMAQ model outl<strong>in</strong>ed <strong>in</strong> A2.1 is used to provide two-day forecast<br />
predictions of PM10 and <strong>PM2.5</strong> and predict how concentrations respond to<br />
reductions <strong>in</strong> precursor emissions of sulphur dioxide (SO2), nitrogen oxides<br />
(NOx) and ammonia (NH3). The CMAQ model described <strong>in</strong> A2.2 is used to<br />
predict hourly concentrations of <strong>PM2.5</strong> at several sites, <strong>in</strong>clud<strong>in</strong>g the rural<br />
(Harwell) and urban background (London North Kens<strong>in</strong>gton) sites. Whilst much<br />
of the temporal variation is captured by the model, predictions of <strong>PM2.5</strong> are<br />
generally 30-40% lower than observed values. Model underpredictions are<br />
also observed <strong>in</strong> other CMAQ modell<strong>in</strong>g discussed <strong>in</strong> A2.3, which considers<br />
the major components that constitute <strong>PM2.5</strong> and shows that model predictions<br />
underestimate some of the major components of <strong>PM2.5</strong> <strong>in</strong> terms of absolute<br />
mass. The estimated relative contributions of each component to total <strong>PM2.5</strong><br />
are, however, similar to observed values.<br />
12. The Lagrangian NAME model described <strong>in</strong> A2.4 shows how an understand<strong>in</strong>g<br />
of the emission sensitivity of <strong>PM2.5</strong> concentrations can be developed. Emission<br />
sensitivity is expressed as a coefficient that provides a measure of how the<br />
concentration of PM changes as a result of a known change <strong>in</strong> emission of<br />
a precursor gas. Such calculations provide useful <strong>in</strong>formation on how <strong>PM2.5</strong><br />
concentrations are likely to respond to controls <strong>in</strong> precursor emissions and can<br />
also reveal important non-l<strong>in</strong>ear behavior between pollutants <strong>in</strong> secondary<br />
particle formation. Annex 2.6 shows the PTM model which has been used to<br />
model <strong>PM2.5</strong> and other species us<strong>in</strong>g detailed chemical schemes. Predictions of<br />
<strong>PM2.5</strong> have been compared with observations and the response of reductions<br />
to precursor emissions on <strong>PM2.5</strong> considered. The PTM model aga<strong>in</strong> captures<br />
important non-l<strong>in</strong>earities <strong>in</strong> the chemical system, which are essential to<br />
understand if policies are to be developed to reduce concentrations of <strong>PM2.5</strong>.<br />
The receptor–oriented Lagrangian model, FRAME, is described <strong>in</strong> A2.7; this<br />
model illustrates the effect of a f<strong>in</strong>er grid resolution, for example with respect<br />
to ammonia emissions and ammonium nitrate formation, and is used to provide<br />
source–receptor relationships for UKIAM.<br />
13. In A2.5 the Eulerian EMEP4UK model is used to predict f<strong>in</strong>e <strong>particulate</strong> nitrate<br />
over seven years at a site <strong>in</strong> Scotland. Longer-term predictions such as these<br />
provide useful <strong>in</strong>formation on trends and also capture important episodes, such<br />
as occurred <strong>in</strong> the spr<strong>in</strong>g of 2003. Similarly, EMEP4UK and the other regionalscale<br />
models can provide surface concentration maps that help to better<br />
understand the spatial distribution of <strong>PM2.5</strong> <strong>in</strong> the UK and Europe.<br />
14. It is noteworthy that the regional-scale models do not predict <strong>PM2.5</strong> mass<br />
directly, but estimate each component that contributes to its mass such as<br />
<strong>particulate</strong> sulphate and nitrate (see Chapter 3). The mass of <strong>PM2.5</strong> is then<br />
calculated from the size distribution of the different components.<br />
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