05.01.2013 Views

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

SHOW MORE
SHOW LESS

Create successful ePaper yourself

Turn your PDF publications into a flip-book with our unique Google optimized e-Paper software.

36. The behaviour of semi-volatile constituents is a major problem both for the<br />

measurement and modell<strong>in</strong>g of <strong>PM2.5</strong>. In the case of measurement, the degree<br />

of partition<strong>in</strong>g of semi-volatile compounds <strong>in</strong>to the measured particles is<br />

determ<strong>in</strong>ed by factors such as atmospheric temperature and relative humidity.<br />

Consequently, if these change dur<strong>in</strong>g the sampl<strong>in</strong>g <strong>in</strong>terval (as they typically<br />

do from day to night), sampl<strong>in</strong>g artefacts can occur through the evaporation<br />

or condensation of such materials from/on the air filter used <strong>in</strong> sampl<strong>in</strong>g.<br />

Additionally, the reduced pressure used to draw air through a sampl<strong>in</strong>g filter<br />

can encourage the vaporisation of semi-volatile components. The difficulties<br />

for modell<strong>in</strong>g start with the prediction of the formation of secondary semivolatile<br />

components and cont<strong>in</strong>ue with the problem of describ<strong>in</strong>g their partition<br />

<strong>in</strong>to the particles. This is affected by many factors, most notably temperature,<br />

relative humidity and the exist<strong>in</strong>g composition of the particles, which affect<br />

the thermodynamic activities of the soluble components and the uptake <strong>in</strong>to<br />

organic films for the hydrophobic components. A further difficulty for modellers<br />

is caused by the fact that air sampl<strong>in</strong>g methods for <strong>PM2.5</strong> are not artefact<br />

free and therefore measure concentrations that may not reflect well the true<br />

airborne suspended particle mass.<br />

37. S<strong>in</strong>ce semi-volatile organic <strong>matter</strong> and ammonium salts comprise a substantial<br />

part of <strong>PM2.5</strong> mass, these issues have major implications for both measurement<br />

and modell<strong>in</strong>g of concentrations.<br />

5.4.4 Other components<br />

38. In addition to primary <strong>PM2.5</strong> from sources represented <strong>in</strong> the emission <strong>in</strong>ventory<br />

and secondary <strong>in</strong>organic aerosol, there is a large contribution from other<br />

components, many of which are more uncerta<strong>in</strong> and <strong>in</strong>clude natural or land<br />

use related contributions not subject to control. These <strong>in</strong>clude rural dust from<br />

w<strong>in</strong>d-suspended soil particles vary<strong>in</strong>g with soil characteristics, and urban dust<br />

<strong>in</strong>clud<strong>in</strong>g material resuspended by traffic. Sea salt is another component of<br />

natural orig<strong>in</strong>, the <strong>in</strong>fluence of which decreases with distance from the coast.<br />

39. F<strong>in</strong>ally, particle bound water makes an additional contribution to particle mass.<br />

It might seem that this is another natural component, but it has been argued<br />

<strong>in</strong> legislation concern<strong>in</strong>g PM10 that it is partly associated with man-made SIA<br />

contributions. However, estimat<strong>in</strong>g any reduction <strong>in</strong> particle bound water <strong>in</strong><br />

response to reductions <strong>in</strong> SO2, NOx and NH3 emissions is extremely uncerta<strong>in</strong>,<br />

<strong>in</strong>volv<strong>in</strong>g both direct and <strong>in</strong>direct effects on cloud processes. Hence, <strong>in</strong> Table 5.5<br />

for example, where water content <strong>in</strong> UKIAM is based on modell<strong>in</strong>g provided<br />

by EMEP, water content is kept constant <strong>in</strong> future projections (which may be<br />

pessimistic). By contrast the PCM model associates the water entirely with the<br />

SIA components and scales it accord<strong>in</strong>gly.<br />

5.5 Model evaluation for <strong>PM2.5</strong><br />

Modell<strong>in</strong>g <strong>PM2.5</strong> and the future<br />

40. Evaluat<strong>in</strong>g models that predict <strong>PM2.5</strong> is complex due to the multiple components<br />

that make up <strong>PM2.5</strong> mass. At one level it is possible to compare absolute mass<br />

predictions directly with <strong>PM2.5</strong> measurements, as illustrated <strong>in</strong> Figure 5.10.<br />

The <strong>in</strong>creased number of sites measur<strong>in</strong>g <strong>PM2.5</strong> <strong>in</strong> recent years will aid model<br />

evaluation <strong>in</strong> this respect. However, while useful, such a comparison is limited<br />

because it will not be known why model predictions depart from measured<br />

values, which is a critical issue for effective model evaluation. For this reason,<br />

139

Hooray! Your file is uploaded and ready to be published.

Saved successfully!

Ooh no, something went wrong!