Quantification of diffuse and fugitive PM10 sources by integrated “hot-spot” method

Between 2002 and 2006, various exceedances of air quality directive 1999/30/EC were reported in a number of PM10 monitoring stations in Flanders. A study was carried out with the objectives: i) to identify and quantify the sources that have caused or have contributed to the exceedances over this period; and ii) to propose suitable emission reduction measures to comply with the current air quality standards (2010). We followed an integrated multi-disciplinary approach consisting of a detailed analysis of the PM10 data series, specific air quality measuring campaigns, air quality modelling and expertise on emission reduction measures (including current BAT and BREF studies). The data analysis was based on 5 steps: 1) The pollution roses of the individual monitoring stations were analyzed. 2) The variation of the PM10 concentration in function of wind speed was assessed to determine whether we were dealing with a fugitive source of primary particles (e.g. mineral dust) or a source of smaller secondary particles taken up and dispersed by the ambient air flow (e.g. industrial combustion sources or traffic sources). 3) The temporal patterns of the potential sources were analyzed. 4) Specific measurement campaigns were organized in the neighbourhood of the potential sources. This included mapping of PM10 concentrations and a detailed analysis of the chemical composition. 5) The (fugitive) PM10 sources were quantified by means of reversed modelling. After deduction of a high background concentration, observed in all monitoring stations in Flanders, results for the individual monitoring stations show that in almost all cases the peak concentrations can be attributed to local fugitive PM10 emissions. Thus for most of the analysed cases it could be concluded that the cause of the exceedances or nearly exceedances is the combination of high background concentrations and local contributions from diffuse or fugitive sources. The total contribution of these non-registered diffuse sources was estimated to be 9–16% of the measured annual averaged PM10 concentrations.

[1]  Guido Cosemans,et al.  Reverse modelling for the determination of fugitive sources of PM10 , 2011 .

[2]  Source apportionment to PM10 in different air quality conditions for Taichung urban and coastal areas, Taiwan , 2004 .

[3]  Michael Sørensen,et al.  On the rate of aeolian sand transport , 2004 .

[4]  A. Venkatram Vertical dispersion of ground-level releases in the surface boundary layer , 1992 .

[5]  M. Viana,et al.  Inter-comparison of receptor models for PM source apportionment: Case study in an industrial area , 2008 .

[6]  H. Tsoar,et al.  Bagnold, R.A. 1941: The physics of blown sand and desert dunes. London: Methuen , 1994 .

[7]  Wolfgang Volkhausen,et al.  Estimating the contribution of industrial facilities to annual PM10 concentrations at industrially influenced sites , 2009 .

[8]  R. Bagnold,et al.  The Physics of Blown Sand and Desert Dunes , 1941 .

[9]  Ronald Greeley,et al.  Wind as a geological process: Wind as a geological process , 1985 .

[10]  Characterisation and quantification of the sources of PM10 during air pollution episodes in the UK. , 2006, The Science of the total environment.

[11]  H. Bultynck,et al.  Evaluation of atmospheric dilution factors for effluents diffused from an elevated continuous point source , 1972 .

[12]  C. Mensink,et al.  Pollutant roses for daily averaged ambient air pollutant concentrations , 2008 .

[13]  P. Hopke,et al.  Source apportionment of particulate matter in Europe: A review of methods and results , 2008 .

[14]  D. Norbäck,et al.  Source apportionment of ambient PM2.5 at five spanish centres of the european community respiratory health survey (ECRHS II) , 2007 .