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 />
48<br />
<strong>PM2.5</strong>/µgm -3<br />
20<br />
15<br />
10<br />
5<br />
0 5<br />
12<br />
hour<br />
18 23<br />
W<strong>in</strong>ter Summer<br />
20<br />
15<br />
10<br />
5<br />
0 5<br />
12<br />
hour<br />
18 23<br />
Figure 3.2: Variation of <strong>PM2.5</strong> concentrations (µg m -3 ) at urban background sites<br />
by hour of the day <strong>in</strong> 2010 at southern UK sites (n=10) <strong>in</strong> w<strong>in</strong>ter and summer.<br />
The shad<strong>in</strong>g represents the 95% confidence <strong>in</strong>terval of the mean.<br />
3.2.2 Diurnal variations of <strong>PM2.5</strong> at roadside and <strong>in</strong>dustrial sites<br />
6. The diurnal patterns for roadside and <strong>in</strong>dustrial sites dur<strong>in</strong>g 2010 are shown<br />
<strong>in</strong> Figure 3.3. The diurnal range is slightly larger at roadside sites than at urban<br />
background sites, while the variation at <strong>in</strong>dustrial sites is broadly similar to<br />
that at urban background sites (cf. Figure 3.1a). However, at roadside sites<br />
the morn<strong>in</strong>g <strong>in</strong>crease is greater and the afternoon dip is less prom<strong>in</strong>ent than<br />
at the urban background sites, with concentrations rema<strong>in</strong><strong>in</strong>g above the early<br />
morn<strong>in</strong>g (03:00-05:00) m<strong>in</strong>imum (cf. Figure 3.3 roadside and Figure 3.1a).<br />
While the morn<strong>in</strong>g peak is consistent with emissions dur<strong>in</strong>g the morn<strong>in</strong>g<br />
rush hour, there is no clear peak dur<strong>in</strong>g the even<strong>in</strong>g rush hour (16:00-18:00),<br />
although concentrations dur<strong>in</strong>g this period are somewhat higher than those<br />
seen <strong>in</strong> the pattern at urban background sites, suggest<strong>in</strong>g an <strong>in</strong>fluence of the<br />
higher traffic flows at this time that is be<strong>in</strong>g masked by chang<strong>in</strong>g background<br />
concentrations, i.e. the traffic <strong>in</strong>crement dur<strong>in</strong>g the rush hour is superimposed<br />
on concentrations that are <strong>in</strong>creas<strong>in</strong>g at this time due to sources contribut<strong>in</strong>g to<br />
the late even<strong>in</strong>g peak, <strong>in</strong>clud<strong>in</strong>g the condensation of semi-volatile species.<br />
A smaller even<strong>in</strong>g traffic-related rush hour peak <strong>in</strong> <strong>PM2.5</strong> is to be expected,<br />
ow<strong>in</strong>g, <strong>in</strong> part, to fewer lorries on the road at this time of day, and to the<br />
greater atmospheric turbulence at this time of day compared to the morn<strong>in</strong>g<br />
rush hour. These effects are also seen <strong>in</strong> the nitrogen oxides (NOx) diurnal<br />
pattern <strong>in</strong> Figure 3.9 later <strong>in</strong> this chapter.<br />
7. The range of diurnal concentrations is much lower at <strong>in</strong>dustrial sites. The<br />
morn<strong>in</strong>g and even<strong>in</strong>g peaks are still evident, suggest<strong>in</strong>g that the background<br />
pattern is play<strong>in</strong>g a dom<strong>in</strong>ant role at these sites with only a m<strong>in</strong>imal<br />
contribution from <strong>in</strong>dustrial activities.