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

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4.7 Summary<br />

<strong>PM2.5</strong> emissions and receptor modell<strong>in</strong>g<br />

98. The major sources of primary emissions of <strong>PM2.5</strong> are combustion <strong>in</strong> the energy<br />

<strong>in</strong>dustries, road transport (both exhaust and non-exhaust emissions), off-road<br />

transport, residential combustion and small-scale waste burn<strong>in</strong>g.<br />

99. Total <strong>PM2.5</strong> emissions for the UK are predicted to decrease significantly by 2020,<br />

with an especially large contribution from reductions <strong>in</strong> road traffic exhaust.<br />

100. The ma<strong>in</strong> traffic sources of <strong>PM2.5</strong> are exhaust emissions from diesel cars, light<br />

goods vehicles and heavy goods vehicles, together with tyre wear, brake wear<br />

and road surface abrasion. A broadly similar picture prevails across the European<br />

Union.<br />

101. There are significant uncerta<strong>in</strong>ties attached to some of these emissions<br />

estimates, particularly to the emissions of <strong>PM2.5</strong> from non-exhaust traffic<br />

sources.<br />

102. With reductions <strong>in</strong> exhaust emissions of PM, non-exhaust components of<br />

traffic emissions will become much more important, emphasis<strong>in</strong>g the need to<br />

<strong>in</strong>troduce measures to control emissions from these non-exhaust traffic sources.<br />

103. Emissions of precursor gases for secondary <strong>PM2.5</strong> components have also been<br />

considered. UK total emissions of NOx have been decl<strong>in</strong><strong>in</strong>g s<strong>in</strong>ce 1999 and are<br />

set to decl<strong>in</strong>e further by 2020. There is some uncerta<strong>in</strong>ty <strong>in</strong> <strong>in</strong>ventories for road<br />

transport emissions for NOx; evidence suggests that vehicle emission directives<br />

have not been effective <strong>in</strong> reduc<strong>in</strong>g “real world” NOx emissions from modern<br />

diesel vehicles manufactured to meet Euro III-V standards. While future road<br />

transport emissions are expected to fall, the rate of reduction may not be as<br />

fast as previous <strong>in</strong>ventory projections have <strong>in</strong>dicated. UK emissions of sulphur<br />

dioxide and non-methane volatile organic compounds have also been decl<strong>in</strong><strong>in</strong>g<br />

and are expected to cont<strong>in</strong>ue to do so. For ammonia, emissions have fallen<br />

only slightly s<strong>in</strong>ce 1990 and are not predicted to fall significantly between 2010<br />

and 2020. EU emissions of NOx have not fallen as rapidly as <strong>in</strong> the UK but are<br />

projected to decl<strong>in</strong>e rapidly by 2020 and significant reductions <strong>in</strong> emissions of<br />

both sulphur dioxide and non-methane volatile organic compounds from the<br />

EU-27 are predicted. On the other hand, emissions of ammonia from the EU-27<br />

are predicted to <strong>in</strong>crease <strong>in</strong> the com<strong>in</strong>g years.<br />

104. Emissions from shipp<strong>in</strong>g are not well quantified. Emissions of NOx and SO2<br />

from shipp<strong>in</strong>g <strong>in</strong> Europe are predicted to <strong>in</strong>crease or only slightly fall <strong>in</strong> the next<br />

decade, although SO2 emissions <strong>in</strong> Sulphur Emission Control Areas around the<br />

UK coast are expected to fall significantly. Without further abatement, emissions<br />

from shipp<strong>in</strong>g will become a more dom<strong>in</strong>ant source of <strong>PM2.5</strong> precursor<br />

emissions <strong>in</strong> Europe.<br />

119

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