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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 />

6<br />

• <strong>PM2.5</strong> emissions from domestic wood burn<strong>in</strong>g, account<strong>in</strong>g for the<br />

effectiveness of control measures;<br />

• biogenic emissions of NMVOCs;<br />

• emissions of NH3 from agriculture, with their temporal as well as spatial<br />

variability;<br />

• exhaust emissions from off-road mach<strong>in</strong>ery used <strong>in</strong> construction and<br />

<strong>in</strong>dustry;<br />

• emissions of SO2 and NOx from shipp<strong>in</strong>g, <strong>in</strong> particular their spatial<br />

distribution around ports and harbours, the temporal variability and future<br />

emissions; and<br />

• exhaust emissions of <strong>PM2.5</strong> from diesel vehicles under real world driv<strong>in</strong>g<br />

conditions and the factors and technologies affect<strong>in</strong>g them.<br />

26. Inventories should be developed to provide a quantification of the spatial and<br />

temporal variability <strong>in</strong> emissions of primary <strong>PM2.5</strong> and its precursors from all<br />

contribut<strong>in</strong>g sources, <strong>in</strong>clud<strong>in</strong>g those not covered <strong>in</strong> national <strong>in</strong>ventories, or<br />

provide the means for calculat<strong>in</strong>g them <strong>in</strong> air <strong>quality</strong> models. Developments<br />

should <strong>in</strong>clude spatially-gridded <strong>in</strong>ventories with high resolution temporal<br />

profiles for different source sectors.<br />

27. Further urgent research on the emissions and atmospheric chemistry of biogenic<br />

volatile organic compounds (VOCs) <strong>in</strong> the context of secondary organic aerosol<br />

formation <strong>in</strong> the UK is required, as this may have significant impact on the<br />

options for mitigation measures. Examples of critical areas have been recently<br />

evaluated. 1<br />

I.4 Modell<strong>in</strong>g and the future<br />

28. Models are an important tool for understand<strong>in</strong>g the l<strong>in</strong>ks between emissions<br />

and observations data and mak<strong>in</strong>g predictions of ambient concentrations <strong>in</strong><br />

a self-consistent framework. Modell<strong>in</strong>g of <strong>PM2.5</strong> rema<strong>in</strong>s a substantial<br />

challenge ow<strong>in</strong>g to uncerta<strong>in</strong>ties <strong>in</strong> and lack of measured data, uncerta<strong>in</strong>ties/<br />

lack of understand<strong>in</strong>g of some aspects of the dynamic, physical and chemical<br />

processes which need to be described with<strong>in</strong> the models, and uncerta<strong>in</strong>ties <strong>in</strong><br />

the emission data and their projections.<br />

29. Several PM models cover<strong>in</strong>g urban to regional scales are used to predict UK<br />

air <strong>quality</strong>. They are based on a range of modell<strong>in</strong>g systems (e.g. Eulerian,<br />

Lagrangian and Gaussian plume). Models are useful for quantify<strong>in</strong>g the different<br />

contributions to PM, e.g. local urban emissions, and the contribution made by<br />

the long-range transport of pollutants.<br />

30. Modell<strong>in</strong>g results have shown that <strong>PM2.5</strong> concentrations exhibit localised<br />

peaks <strong>in</strong> urban areas, ow<strong>in</strong>g to local sources of primary <strong>PM2.5</strong>, superimposed<br />

on a regional background. These local sources are generally well represented<br />

by models, except when close to roads with complex street geometries. An<br />

1 EPRI and A&WMA Workshop on Future <strong>Air</strong> Quality Model Development Needs, 12-13 September 2011, Wash<strong>in</strong>gton, D.C., USA.

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