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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 />

70<br />

43. The UK has <strong>in</strong>itiated a monitor<strong>in</strong>g programme to meet the Directive<br />

requirements <strong>in</strong> respect of PM composition. MARGA <strong>in</strong>struments were <strong>in</strong>stalled<br />

at Auchencorth Moss (located to the south of Ed<strong>in</strong>burgh) <strong>in</strong> 2006 and at<br />

Harwell (located to the south of Oxford) <strong>in</strong> 2009. These <strong>in</strong>struments specifically<br />

measure the species listed above <strong>in</strong> the <strong>PM2.5</strong> and PM10 fractions on an hourly<br />

basis (but not Fe). The data have been exam<strong>in</strong>ed carefully by AQEG, but<br />

concerns about their <strong>quality</strong> make them unsuitable for analysis. These concerns<br />

<strong>in</strong>clude concentrations be<strong>in</strong>g higher <strong>in</strong> the <strong>PM2.5</strong> fraction than the PM10 fraction<br />

and a lack of ionic balance. It is therefore recommended that the suitability<br />

of these <strong>in</strong>struments for meet<strong>in</strong>g report<strong>in</strong>g obligations under the<br />

Directive is reviewed.<br />

44. Monitor<strong>in</strong>g of total ambient nitrate, sulphate and ammonium concentrations<br />

has been undertaken over a number of years at sites across the UK (see Chapter<br />

2). Although these measurements are not specifically for the <strong>PM2.5</strong> size fraction,<br />

the results are still useful for an analysis of seasonal patterns and trends.<br />

3.9.3 Seasonal pattern of nitrate and sulphate<br />

45. The UK Acid Gases and Aerosols Monitor<strong>in</strong>g Network (AGANet) has been <strong>in</strong><br />

operation s<strong>in</strong>ce 1999, with 12 orig<strong>in</strong>al sites expanded to 30 sites <strong>in</strong> 2006. This<br />

Network records monthly mean concentrations. The seasonal pattern across<br />

all sites and all years is shown <strong>in</strong> Figure 3.18. The shaded area represents the<br />

uncerta<strong>in</strong>ty <strong>in</strong> the mean value for each month at the 95% confidence level,<br />

it does not represent the overall measurement of uncerta<strong>in</strong>ty. There is clear<br />

evidence of a nitrate peak <strong>in</strong> the early spr<strong>in</strong>g (~3 µg m -3 ), <strong>in</strong> particular <strong>in</strong> March<br />

and April, before a rapid drop to relatively constant concentrations for the rest<br />

of the year (~1.5 µg m -3 ). The sulphate concentrations are also highest <strong>in</strong> March<br />

and April (~1.4 µg m -3 ), but show only a slow decl<strong>in</strong>e over the summer, with the<br />

lowest concentrations occurr<strong>in</strong>g <strong>in</strong> the w<strong>in</strong>ter months (0.8-1.0 µg m -3 ).<br />

NO 2<br />

30<br />

25<br />

20<br />

15<br />

Nitrate<br />

J F M A M J J A S O N D<br />

month<br />

SO 4<br />

14<br />

12<br />

10<br />

08<br />

Sulphate<br />

J F M A M J J A S O N D<br />

month<br />

Figure 3.18: Variation of nitrate and sulphate concentrations (µg m -3 ) by month<br />

of the year (data from 30 AGANet sites, 1999-2009). The shad<strong>in</strong>g represents<br />

the 95% confidence <strong>in</strong>terval of the mean. Note different scales.

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