Abstract

Abstract. Sub-50 nm particles originating from traffic emissions pose risks to human health due to their high lung deposition efficiency and potentially harmful chemical composition. We present a modeling study using an updated European Aerosol Cloud Climate and Air Quality Interactions (EUCAARI) number emission inventory, incorporating a more realistic, empirically justified particle size distribution (PSD) for sub-50 nm particles from road traffic as compared with the previous version. We present experimental PSDs and CO2 concentrations, measured in a highly trafficked street canyon in Helsinki, Finland, as an emission factor particle size distribution (EFPSD), which was then used in updating the EUCAARI inventory. We applied the updated inventory in a simulation using the regional chemical transport model PMCAMx-UF over Europe for May 2008. This was done to test the effect of updated emissions at regional and local scales, particularly in comparison with atmospheric new particle formation (NPF). Updating the inventory increased the simulated average total particle number concentrations by only 1 %, although the total particle number emissions were increased to a 3-fold level. The concentrations increased up to 11 % when only 1.3–3 nm sized particles (nanocluster aerosol, NCA) were considered. These values indicate that the effect of updating overall is insignificant at a regional scale during this photochemically active period. During this period, the fraction of the total particle number originating from atmospheric NPF processes was 91 %; thus, these simulations give a lower limit for the contribution of traffic to the aerosol levels. Nevertheless, the situation is different when examining the effect of the update closer spatially or temporally or when focusing on the chemical composition or the origin of the particles. For example, the daily average NCA concentrations increased by a factor of several hundred or thousand in some locations on certain days. Overall, the most significant effects – reaching several orders of magnitude – from updating the inventory are observed when examining specific particle sizes (especially 7–20 nm), particle components, and specific urban areas. While the model still has a tendency to predict more sub-50 nm particles compared to the observations, the most notable underestimations in the concentrations of sub-10 nm particles are now overcome. Additionally, the simulated distributions now agree better with the data observed at locations with high traffic densities. The findings of this study highlight the need to consider emissions, PSDs, and composition of sub-50 nm particles from road traffic in studies focusing on urban air quality. Updating this emission source brings the simulated aerosol levels, particularly in urban locations, closer to observations, which highlights its importance for calculations of human exposure to nanoparticles.

Highlights

  • Detailed emission inventories are necessary for predictions of air quality and atmospheric composition in general

  • Road-transport-related particle number emission factors were determined from measurements performed at the curbside of an urban street canyon in Helsinki, Finland

  • Deriving an emission factor particle size distribution (EFPSD) from bin-by-bin calculation of emission factors was found to be an acceptable method based on the agreement with the reported difference between the particle size distribution (PSD) measured with wind blowing from the road and from the background direction

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Summary

Introduction

Detailed emission inventories are necessary for predictions of air quality and atmospheric composition in general. While road transport is a significant particle source in areas affected by vehicles, such as in urban environments (Shi et al, 2001; Kumar et al, 2014), the EUCAARI inventory, does not fully consider the traffic-originated emissions of the smallest (especially sub-50 nm in diameter, Dp) particles. This results partially from the fact that only nonvolatile particles larger than 23 nm have been selected as the regulated ones in current road transport number emission standards (Giechaskiel et al, 2012) because measuring them is far more reproducible than measuring volatile ones. Ments – trends of urban aerosol and vehicle emissions were used to scale the determined emissions from 2017 to 2008

Experimental data
Determining traffic emission factors
Atmospheric measurement stations
Simulations
Model description
Updating the emission inventory
Emission factor particle size distribution
Uncertainties involved in updating the emission inventory
Comparing simulated particle number concentrations with observations
Effect of updating emission inventory on relative particle concentrations
Comparing simulated particle size distributions with observations
Change in particle composition after updating the emission inventory
Findings
Summary and conclusions
Full Text
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