Model used in « Source Apportionment of Airborne Particulate Matter in the UK » [Stedman et al.,...

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Model used in « Source Apportionment of Airborne Particulate Matter in the UK » [Stedman et al., Receptor modelling of PM 10 concentrations at a UK national network monitoring site in central London, Atmospheric environment (35) 297-304 (2000)] PM 10 = A * [NOx urban] (surrogate of PM from local combustion) +B * [SO 4 rural] (surrogate of secondary regional PM ) +C (other PM : crustal material, marine aerosol,…) Statistical model of PM10 origin in the urban atmosphere -CLRTAP and EMEP Task Force on Integrated Assessment Modelling session, Oslo, 13-15 May 2002

Transcript of Model used in « Source Apportionment of Airborne Particulate Matter in the UK » [Stedman et al.,...

Page 1: Model used in « Source Apportionment of Airborne Particulate Matter in the UK » [Stedman et al., Receptor modelling of PM 10 concentrations at a UK national.

• Model used in « Source Apportionment of Airborne Particulate Matter in the UK » [Stedman et al., Receptor modelling of PM10 concentrations at a UK national network monitoring site in central London, Atmospheric environment (35) 297-304 (2000)]

• PM10 = A * [NOx urban] (surrogate of PM from local combustion)

+B * [SO4 rural] (surrogate of secondary regional PM )

+C (other PM : crustal material, marine aerosol,…)

Statistical model of PM10 origin in the urban atmosphere

UNECE-CLRTAP and EMEP Task Force on Integrated Assessment Modelling27th session, Oslo, 13-15 May 2002

Page 2: Model used in « Source Apportionment of Airborne Particulate Matter in the UK » [Stedman et al., Receptor modelling of PM 10 concentrations at a UK national.

Location of cities (blue) and rural SO4 monitoring stations (red)

UNECE-CLRTAP and EMEP Task Force on Integrated Assessment Modelling27th session, Oslo, 13-15 May 2002

Page 3: Model used in « Source Apportionment of Airborne Particulate Matter in the UK » [Stedman et al., Receptor modelling of PM 10 concentrations at a UK national.

Clermont-Ferrand : comparison between model and observations

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MeasuredPM13Concentration

ModelledPM13concentrations

UNECE-CLRTAP and EMEP Task Force on Integrated Assessment Modelling27th session, Oslo, 13-15 May 2002

Page 4: Model used in « Source Apportionment of Airborne Particulate Matter in the UK » [Stedman et al., Receptor modelling of PM 10 concentrations at a UK national.

Clermont-Ferrand : variability of local and regional contributions to

ambient PM

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Contribution oflocalcombustion

Contribution ofregional PM

UNECE-CLRTAP and EMEP Task Force on Integrated Assessment Modelling27th session, Oslo, 13-15 May 2002

Page 5: Model used in « Source Apportionment of Airborne Particulate Matter in the UK » [Stedman et al., Receptor modelling of PM 10 concentrations at a UK national.

Paris : seasonnality of local and regional contributions to ambient

PM

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Measured PM10concentration

Estimatedcontribution fromlocal combustions

Estimatedcontribution fromregional PM

UNECE-CLRTAP and EMEP Task Force on Integrated Assessment Modelling27th session, Oslo, 13-15 May 2002

Page 6: Model used in « Source Apportionment of Airborne Particulate Matter in the UK » [Stedman et al., Receptor modelling of PM 10 concentrations at a UK national.

Overview of local/regionalcontributions for four

cities

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Clermont-Ferrand Caen

Paris 12ème Vitry-sur-Seine (Paris suburban)

UNECE-CLRTAP and EMEP Task Force on Integrated Assessment Modelling27th session, Oslo, 13-15 May 2002

Page 7: Model used in « Source Apportionment of Airborne Particulate Matter in the UK » [Stedman et al., Receptor modelling of PM 10 concentrations at a UK national.

Refined model for PM apportionment in a Suburban Paris site

• Both PM10 and PM2.5 being available at Vitry (suburban Paris), a more refined apportionment model has been applied, identifying specifically the contribution of coarse particles (construction, road abrasion, brake and tyre wear, construction, mineral dust,...). This contribution amounts to 36% of ambiant PM10.

• Mean unexplained PM10 concentration is below 1 µg/m3• The « local combustion » and « regional PM » , as identified

by the model, are almost enterely in the PM2.5 size range.• For this suburban Paris site, the share of « local combustion »

in PM2.5 ambiant concentration is higher than that for PM10 (70% for PM2.5 versus 50% for PM10).

Page 8: Model used in « Source Apportionment of Airborne Particulate Matter in the UK » [Stedman et al., Receptor modelling of PM 10 concentrations at a UK national.

Refined model for PM apportionment in a Suburban Paris site : results for

PM10.

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Measured concentrations

Estimated contribution fromlocal combustion

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Estimated share of coarseparticules (both local orlong-range)

Page 9: Model used in « Source Apportionment of Airborne Particulate Matter in the UK » [Stedman et al., Receptor modelling of PM 10 concentrations at a UK national.

Refined model for PM apportionment in a Suburban Paris site : results for PM2.5

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Estimatedcontribution fromregional PM

Page 10: Model used in « Source Apportionment of Airborne Particulate Matter in the UK » [Stedman et al., Receptor modelling of PM 10 concentrations at a UK national.

Some concluding remarks

• Both local sources and regional concentrations are important to explain ambiant PM10 concentration in the cities studied here.

• Local combustion involved through: - Transport : primary PM, secondary PM from NOx

and VOC emissions. - Heating : the case of Paris in winter ??

• The share of local combustion increases when considering PM2.5 instead of PM10 for the case in suburban Paris studied.

UNECE-CLRTAP and EMEP Task Force on Integrated Assessment Modelling27th session, Oslo, 13-15 May 2002