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Air quality expert group - Fine particulate matter (PM2.5) in ... - Defra

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<strong>PM2.5</strong>/µgm -3<br />

20<br />

15<br />

10<br />

5<br />

Roadside<br />

0 5<br />

12<br />

hour<br />

18 23<br />

20<br />

15<br />

10<br />

5<br />

Concentrations and composition of <strong>PM2.5</strong><br />

Industrial<br />

0 5<br />

12<br />

hour<br />

18 23<br />

Figure 3.3: Variation of <strong>PM2.5</strong> concentrations (µg m -3 ) by hour of the day at<br />

roadside (n=9) and <strong>in</strong>dustrial sites (n=4) <strong>in</strong> 2010. The shad<strong>in</strong>g represents the<br />

95% confidence <strong>in</strong>terval of the mean.<br />

3.2.3 Diurnal variations at a site <strong>in</strong> Lisburn, Northern Ireland<br />

8. Laxen et al. (2010) noted that the site <strong>in</strong> Lisburn, Northern Ireland, was<br />

anomalous, show<strong>in</strong>g much higher concentrations <strong>in</strong> 2009 that expected. This<br />

anomaly was reta<strong>in</strong>ed <strong>in</strong> 2010, with a much greater diurnal variation <strong>in</strong> <strong>PM2.5</strong><br />

concentrations (Figure 3.4). The range over the day is around five times greater<br />

than at other urban background sites (cf. Figure 3.1). This is primarily due to<br />

high overnight concentrations at this site, which peak at a similar time to the<br />

peaks seen at other background sites (cf. Figure 3.2). It is suspected that these<br />

high concentrations are due to domestic heat<strong>in</strong>g, which is still supplied <strong>in</strong> part<br />

by solid fuel <strong>in</strong> Northern Ireland. This is supported by the observation that the<br />

even<strong>in</strong>g peak is much larger dur<strong>in</strong>g the w<strong>in</strong>ter than the summer (not shown).<br />

It is similar to the pattern for black carbon concentrations at Strabane (Figure<br />

3.23), which has also been ascribed to domestic heat<strong>in</strong>g. The night-time peak<br />

will also relate to the more stable atmospheric conditions at night, which will<br />

enhance the impact of local emissions at this time. Clearly domestic solid<br />

and/or liquid fuel used for domestic heat<strong>in</strong>g can be a significant source<br />

of <strong>PM2.5</strong>, with black carbon be<strong>in</strong>g a major constituent. This source makes<br />

its most significant contribution dur<strong>in</strong>g the even<strong>in</strong>g.<br />

<strong>PM2.5</strong>/µgm -3<br />

30<br />

20<br />

10<br />

0 5<br />

12<br />

hour<br />

18 23<br />

30<br />

20<br />

10<br />

J F M A M J<br />

hour<br />

J A S O N O<br />

Figure 3.4: Variation of <strong>PM2.5</strong> concentrations (µg m<br />

49<br />

-3 ) by hour of the day and<br />

month of the year at the Lisburn site <strong>in</strong> Northern Ireland <strong>in</strong> 2010. The shad<strong>in</strong>g<br />

represents the 95% confidence <strong>in</strong>terval of the mean. Note the different scale to<br />

the other figures.

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