Vehicle nanoparticle emissions under transient driving conditions
Karjalainen, Panu (2014)
Karjalainen, Panu
Tampere University of Technology
2014
Luonnontieteiden ja ympäristötekniikan tiedekunta - Faculty of Science and Environmental Engineering
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Julkaisun pysyvä osoite on
https://urn.fi/URN:ISBN:978-952-15-3442-3
https://urn.fi/URN:ISBN:978-952-15-3442-3
Tiivistelmä
Real-world driving consist mostly of transients, where the engine parameters are constantly changing. In emission regulation this has been partially considered by including transient driving cycles in emission standards. However, specific particle emissions data for detailed driving conditions have remained limited. This thesis covers results of transient exhaust particle emissions, including both diesel and gasoline engines. The experiments were performed in laboratories and on the road. The focus was always on the real-world particle emissions.
During transient cycles both heavy-duty (HD) diesel engines and light-duty (LD) gasoline vehicles produced elevated soot particle concentrations during accelerations. For instance, in on-road experiment of a LD gasoline vehicle, the exhaust plume particle concentrations at steady speeds were at clean ambient levels, but during accelerations concentrations were 10-50 times the background level. For gasoline vehicles the soot particle size distributions were bi-modal in nature. Currently neither LD gasoline nor nonroad HD diesel engines necessarily need to employ particle filtration in the exhaust system in order to meet the demands of the relevant legislation.
Sulfur originating in the fuel or lubricant oil can be stored inside catalysts, and later be released, forming semivolatile nucleation mode (NM) particles when temperature rises. This behavior was detected for LD and HD engines in the engine laboratory, for a HD vehicle on the road and in a simplified measurement setup in an aerosol laboratory. The aerosol laboratory test indicated that the NM formation does not necessarily require hydrocarbons or sulfated hydrocarbons; particles are electrically neutral and evaporate when they undergo thermal treatment. While sulfur is released from the catalysts, the HD road engine study indicated that the increased NM particle emission is not explained by the concentration of gaseous sulfuric acid. The sulfur storage and release depends greatly on the driving history, also due to this NM particle emissions seem plausible, even with low sulfur fuels. With catalytic particle filters, the amount of soot is reduced, promoting semivolatile NM particle emissions.
An unexpected observation was made that some engines produce nanoparticles containing lubricant oil derived metals during driving while not fueled. Exhaust particles were observed during engine braking events for a HD truck and LD gasoline vehicles. For the truck and gasoline vehicles, the engine braking related particles contributed up to 20-30% and 3-30% of the total number emissions, respectively. These particle emissions can be a reality for all vehicle types not using particle filtration, including the latest technology vehicles. In particle filters, engine braking related particles can affect the ash accumulation and transport mechanisms.
During transient cycles both heavy-duty (HD) diesel engines and light-duty (LD) gasoline vehicles produced elevated soot particle concentrations during accelerations. For instance, in on-road experiment of a LD gasoline vehicle, the exhaust plume particle concentrations at steady speeds were at clean ambient levels, but during accelerations concentrations were 10-50 times the background level. For gasoline vehicles the soot particle size distributions were bi-modal in nature. Currently neither LD gasoline nor nonroad HD diesel engines necessarily need to employ particle filtration in the exhaust system in order to meet the demands of the relevant legislation.
Sulfur originating in the fuel or lubricant oil can be stored inside catalysts, and later be released, forming semivolatile nucleation mode (NM) particles when temperature rises. This behavior was detected for LD and HD engines in the engine laboratory, for a HD vehicle on the road and in a simplified measurement setup in an aerosol laboratory. The aerosol laboratory test indicated that the NM formation does not necessarily require hydrocarbons or sulfated hydrocarbons; particles are electrically neutral and evaporate when they undergo thermal treatment. While sulfur is released from the catalysts, the HD road engine study indicated that the increased NM particle emission is not explained by the concentration of gaseous sulfuric acid. The sulfur storage and release depends greatly on the driving history, also due to this NM particle emissions seem plausible, even with low sulfur fuels. With catalytic particle filters, the amount of soot is reduced, promoting semivolatile NM particle emissions.
An unexpected observation was made that some engines produce nanoparticles containing lubricant oil derived metals during driving while not fueled. Exhaust particles were observed during engine braking events for a HD truck and LD gasoline vehicles. For the truck and gasoline vehicles, the engine braking related particles contributed up to 20-30% and 3-30% of the total number emissions, respectively. These particle emissions can be a reality for all vehicle types not using particle filtration, including the latest technology vehicles. In particle filters, engine braking related particles can affect the ash accumulation and transport mechanisms.
Kokoelmat
- Väitöskirjat [4848]