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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<strong>PM2.5</strong> <strong>in</strong> the UK<br />
68<br />
3.9 Composition<br />
3.9.1 Overall composition of <strong>PM2.5</strong><br />
39. There have been few measurements of the overall composition of <strong>PM2.5</strong> <strong>in</strong> the<br />
UK. Y<strong>in</strong> and Harrison (2008) collected 24-hour samples of <strong>PM2.5</strong> from three<br />
sites <strong>in</strong> and around Birm<strong>in</strong>gham between 2004 and 2006, sampl<strong>in</strong>g daily at a<br />
central urban background site (12 months), a roadside site (six months, ma<strong>in</strong>ly<br />
summer) and a rural site (six months, ma<strong>in</strong>ly w<strong>in</strong>ter). Samples were taken<br />
sequentially. A pragmatic mass closure model was used to assign compounds<br />
to the measured constituents. This mass closure model is a way of account<strong>in</strong>g<br />
for the measured mass concentration of airborne particles by summ<strong>in</strong>g scaled<br />
values of the concentrations of major chemical components <strong>in</strong> such a way as<br />
to allow for those components that are not directly measured (Harrison et al.,<br />
2003). The overall results for the central urban background site are shown <strong>in</strong><br />
Figure 3.17a. Three components account for a large proportion of the total<br />
mass: nitrate, sulphate and organics. Iron-rich dusts are attributed to nonexhaust<br />
traffic emissions, calcium salts are attributed to construction/demolition<br />
dust and w<strong>in</strong>d-blown soil, and sodium chloride to sea salt (although this should<br />
also <strong>in</strong>clude resuspended de-ic<strong>in</strong>g salt). Elemental carbon relates to primary<br />
combustion. Organic carbon (organics), both from combustion and natural<br />
sources, may be either primary or secondary.<br />
40. Y<strong>in</strong> and Harrison (2008) also reported the <strong>PM2.5</strong> composition on high pollution<br />
episode days (i.e. days with daily mean PM10 > 50 µg m -3 ). They reported a<br />
substantial <strong>in</strong>crease <strong>in</strong> nitrate, which accounts for just under half the <strong>PM2.5</strong><br />
on episode days (Figure 3.17b). The authors note that this emphasises the<br />
importance of develop<strong>in</strong>g a better understand<strong>in</strong>g of the sources of nitrate <strong>in</strong><br />
airborne PM. Putaud et al. (2010) also report higher nitrate contributions at<br />
higher <strong>PM2.5</strong> concentrations based on measurements carried out elsewhere<br />
<strong>in</strong> Europe.<br />
41. Measurements of chemical composition are important for source apportionment<br />
and it is recommended that further measurements should be made of<br />
chemical composition <strong>in</strong> a variety of locations, pr<strong>in</strong>cipally rural, urban<br />
background and roadside, over different parts of the UK, to allow source<br />
apportionment to be conducted.