Technical note: Emission factors, chemical composition, and morphology of particles emitted from Euro 5 diesel and gasoline light-duty vehicles during transient cycles

被引:31
作者
Kostenidou, Evangelia [1 ]
Martinez-Valiente, Alvaro [2 ]
R'Mili, Badr [1 ]
Marques, Baptiste [1 ]
Temime-Roussel, Brice [1 ]
Durand, Amandine [1 ]
Andre, Michel [3 ]
Liu, Yao [3 ]
Louis, Cedric [3 ]
Vansevenant, Boris [3 ]
Ferry, Daniel [4 ]
Laffon, Carine [4 ]
Parent, Philippe [4 ]
D'Anna, Barbara [1 ]
机构
[1] Aix Marseille Univ, LCE, CNRS, Marseille, France
[2] Univ Lyon, IRCELYON, UMR 5256, CNRS, Villeurbanne, France
[3] Univ Gustave Eiffel, Univ Lyon, IFSTTAR, AME EASE, Lyon, France
[4] Aix Marseille Univ, CINaM, CNRS, Marseille, France
关键词
POLYCYCLIC AROMATIC-HYDROCARBONS; ORGANIC AEROSOL FORMATION; DIRECT-INJECTION GDI; PARTICULATE MATTER EMISSIONS; HIGH-RESOLUTION; ON-ROAD; COLD-START; ULTRAFINE PARTICLES; TRAFFIC EMISSIONS; MASS-SPECTROMETRY;
D O I
10.5194/acp-21-4779-2021
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
Changes in engine technologies and after-treatment devices can profoundly alter the chemical composition of the emitted pollutants. To investigate these effects, we characterized the emitted particles' chemical composition of three diesel and four gasoline Euro 5 light-duty vehicles tested at a chassis dynamometer facility. The dominant emitted species was black carbon (BC) with emission factors (EFs) varying from 0.2 to 7.1 mg km(-1) for direct-injection gasoline (GDI) vehicles, from 0.02 to 0.14 mg km(-1) for port fuel injection (PFI) vehicles, and 0.003 to 0.9 mg km(-1) for diesel vehicles. The organic matter (OM) EFs varied from 5 to 103 mu g km(-1) for GDI gasoline vehicles, from 1 to 8 mu g km(-1) for PFI vehicles, and between 0.15 and 65 mu g km(-1) for the diesel vehicles. The first minutes of cold-start cycles contributed the largest PM fraction including BC, OM, and polycyclic aromatic hydrocarbons (PAHs). Using a high-resolution time-of-flight mass spectrometer (HR-ToF-AMS), we identified more than 40 PAHs in both diesel and gasoline exhaust particles including methylated, nitro, oxygenated, and amino PAHs. Particle-bound PAHs were 4 times higher for GDI than for PFI vehicles. For two of the three diesel vehicles the PAH emissions were below the detection limit, but for one, which presented an after-treatment device failure, the average PAHs EF was 2.04 mu g km(-1), similar to the GDI vehicle's values. During the passive regeneration of the catalysed diesel particulate filter (CDPF) vehicle, we measured particles of diameter around 15 nm mainly composed of ammonium bisulfate. Transmission electron microscopy (TEM) images revealed the presence of ubiquitous metal inclusions in soot particles emitted by the diesel vehicle equipped with a fuelborne-catalyst diesel particulate filter (FBC-DPF). X-ray photoelectron spectroscopy (XPS) analysis of the particles emitted by the PFI vehicle showed the presence of metallic elements and a disordered soot surface with defects that could have consequences on both chemical reactivity and particle toxicity. Our findings show that different after-treatment technologies have an important effect on the emitted particles' levels and their chemical composition. In addition, this work highlights the importance of particle filter devices' condition and performance.
引用
收藏
页码:4779 / 4796
页数:18
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