Abstract

Road transport significantly contributes to air pollution in cities. Emission regulations have led to significantly reduced emissions in modern vehicles. Particle emissions are controlled by a particulate matter (PM) mass and a solid particle number (SPN) limit. There are concerns that the SPN limit does not effectively control all relevant particulate species and there are instances of semi-volatile particle emissions that are order of magnitudes higher than the SPN emission levels. This overview discusses whether a new metric (total particles, i.e., solids and volatiles) should be introduced for the effective regulation of vehicle emissions. Initially, it summarizes recent findings on the contribution of road transport to particle number concentration levels in cities. Then, both solid and total particle emission levels from modern vehicles are presented and the adverse health effects of solid and volatile particles are briefly discussed. Finally, the open issues regarding an appropriate methodology (sampling and instrumentation) in order to achieve representative and reproducible results are summarized. The main finding of this overview is that, even though total particle sampling and quantification is feasible, details for its realization in a regulatory context are lacking. It is important to define the methodology details (sampling and dilution, measurement instrumentation, relevant sizes, etc.) and conduct inter-laboratory exercises to determine the reproducibility of a proposed method. It is also necessary to monitor the vehicle emissions according to the new method to understand current and possible future levels. With better understanding of the instances of formation of nucleation mode particles it will be possible to identify its culprits (e.g., fuel, lubricant, combustion, or aftertreatment operation). Then the appropriate solutions can be enforced and the right decisions can be taken on the need for new regulatory initiatives, for example the addition of total particles in the tailpipe, decrease of specific organic precursors, better control of inorganic precursors (e.g., NH3, SOx), or revision of fuel and lubricant specifications.

Highlights

  • The atmospheric aerosol is a complex and dynamic mixture of solid and liquid particles in the air, generated from natural and anthropogenic sources

  • The aim of the current study is to answer the question: is it necessary to change the current solid particle number (SPN) approach and include smaller particles and those of higher volatility? To answer this question this review summarizes the current status on various topics: (i) road transport contribution to ambient particulate matter (PM) mass and number; (ii) PM mass, number emissions and potential for secondary aerosol formation from vehicles and comparison between solid and total particle number (TPN) emissions; and (iii) technical feasibility of measuring total particles

  • In the European Union (EU) particulate emissions from vehicles have to fulfill a particulate matter (PM) mass limit, and a solid particle number (SPN) limit for particles >23 nm, that may be extended in the future to cover particles >10 nm

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Summary

Introduction

The atmospheric aerosol is a complex and dynamic mixture of solid and liquid particles in the air, generated from natural (such as pollen, sea salt, volcanic ash, and soot particles from natural fires) and anthropogenic sources (e.g., combustion, waste incineration, and road abrasion). The secondary organic aerosol (SOA) originates from volatile organic compounds (VOCs) which undergo gas phase oxidation reactions, forming products that have low enough volatility to form aerosol either via nucleation or condensation onto pre-existing particles [23]. Intermediate volatility organic compounds (IVOCs) partition almost entirely to the gas phase upon dilution to atmospheric conditions [30] They are highly prone to SOA formation during their gradual oxidation in the atmosphere [33,34]. Semi-volatile organic compounds (SVOCs) are partitioned between the gaseous and condensed phases already during primary emission [35]. Their further oxidation practically shifts their partition entirely to the particulate phase.

Air Quality Legislation
Vehicle Emissions Standards
PM in Cities
Ultrafine Particles in Cities
PM Emitted from Vehicles
Definitions
Primary “Tailpipe” Particles
Delayed Primary “Fresh” Particles
Secondary Particles
Health Effects of Particles
Sampling Conditions
Diluter and Particle Losses
Findings
Conclusions
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