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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 />

56<br />

Correlation<br />

0.8<br />

0.6<br />

0.4<br />

0.2<br />

all data<br />

0 50<br />

100<br />

Distance (km)<br />

Figure 3.10: Correlation coefficients of hourly mean <strong>PM2.5</strong> concentrations<br />

(µg m -3 ) at 11 urban background sites <strong>in</strong> the Thames Valley area of southern<br />

England as a function of distance between the sites (Laxen et al., 2010). The<br />

shad<strong>in</strong>g represents 95% confidence <strong>in</strong>terval.<br />

3.5.2 Differences <strong>in</strong> annual mean <strong>PM2.5</strong> concentrations by site type<br />

21. Laxen et al. (2010) <strong>in</strong> their summary of 2009 annual mean <strong>PM2.5</strong> concentrations<br />

reported that urban background concentrations <strong>in</strong> major urban areas were<br />

around 3-6 µg m -3 above the rural background, 3 while concentrations alongside<br />

busy roads were around 1-2 µg m -3 above the urban background, ris<strong>in</strong>g to 7-8<br />

µg m -3 above the urban background at the kerbside (with<strong>in</strong> 1 m of the kerb)<br />

of busy roads. Thus <strong>in</strong> the south of England, where the rural background is<br />

around 10-11 µg m -3 , the urban background concentrations are around 13-17<br />

µg m -3 . This is the pattern illustrated <strong>in</strong> the transect of modelled background<br />

concentrations across London <strong>in</strong> Figure 5.6 <strong>in</strong> Chapter 5. The kerbside<br />

concentrations would then be up to 20-25 µg m -3 . Clearly the rural background<br />

is a dom<strong>in</strong>ant contributor to <strong>PM2.5</strong> concentrations at urban background sites,<br />

but as Laxen et al. (2010) observed, only two rural sites provided data <strong>in</strong> 2009<br />

(Auchencorth Moss and Harwell). The same was true for 2010. Two sites are<br />

not considered sufficient to def<strong>in</strong>e the spatial distribution of rural background<br />

concentrations across the UK. Laxen et al. (2010) recommended that seven<br />

additional <strong>PM2.5</strong> monitors should be set up at rural sites as a m<strong>in</strong>imum and<br />

that these could usefully be located at exist<strong>in</strong>g ozone monitor<strong>in</strong>g sites. AQEG<br />

agrees that there are too few rural monitors to properly def<strong>in</strong>e the important<br />

rural background contribution to <strong>PM2.5</strong> across the UK. Additional sites will help<br />

3 The term ‘rural background’ is treated as be<strong>in</strong>g synonymous with ‘regional background’. Rural monitor<strong>in</strong>g sites must be located away<br />

from local sources.

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