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Investigations of nanoparticle emissions of two gasoline cars MPI & DI at stationary part load operation

Czerwiński J., Comte P., Keller A., Mayer A.

Combustion Engines

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2014

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R. 53, nr 3

3--11

EN

Starting from Euro 6 not only for diesel but also for gasoline vehicles, with direct injection technology (GDI) a solid particle number emissions limit of 6 × 1011#/km becomes effective. The limit was temporary extended for GDI to 6 x 1012#/km. Nuclei of metals as well as organics are suspected to significantly contribute especially to the ultrafine particle size fractions, and thus to the particle number concentration. In the project GasOMeP (Gasoline Organic & Metal Particulates) metal-nanoparticles (including sub 20 nm) from gasoline cars are investigated for different engine technologies. In the present paper some results of basic investigations of nanoparticles from two gasoline cars – an older one with MPI and a never one with DI – are represented. The measurements were performed at vehicle tailpipe, with varying sampling conditions and with different SMPS-systems, which enabled the mobility scanning in different size ranges. The results show that the older vehicle with MPI emits high particle count concentrations. The size distributions are decisively bimodal with high numbers in nuclei mode. In this case, the particle counting below 10 nm yields important information. The emissions of the newer vehicle with DI show no typical uniform shape of particle size distributions and are at lower level, than for the older vehicle. There is no visible nuclei mode and the ultrafine particle concentrations below 10 nm are insignificant. A sampling with a strongly increased primary dilution has a clear influence on the indicated (higher) particle concentrations.

PL

Począwszy od normy Euro 6 wprowadzone zostanie ograniczenie emisji cząstek stałych do 6 × 1011#/km nie tylko dla pojazdów wyposażonych w silniki ZS, ale także dla pojazdów z silnikami ZI z bezpośrednim wtryskiem paliwa (GDI). Dopuszczalna liczba cząstek stałych emitowanych przez pojazdy wyposażone w silniki GDI była tymczasowo zwiększona do 6 × 1012#/km. Cząstki metali, jak również substancje organiczne prawdopodobnie są powodem emisji bardzo małych cząstek stałych, przyczyniając się do zwiększenia liczby emitowanych cząstek stałych. W projekcie GasOMeP (cząstki organiczne i metalowe z silników benzynowych) badana jest emisja nanocząstek metali (również o średnicy < 20 nm) z samochodów wyposażonych w silniki benzynowe różnych generacji. W artykule przedstawiono wyniki badań emisji nanocząstek z dwóch samochodów wyposażonych w silniki benzynowe – starszy z wtryskiem MPI i nowszy z wtryskiem DI. Spaliny pobierano z układu wylotowego pojazdu przy różnych warunkach pomiarowych i z wykorzystaniem urządzeń do pomiaru emisji cząstek stałych o różnych zakresach pomiarowych. Wyniki badań wskazują, że stężenie cząstek stałych w spalinach starszego pojazdu z wtryskiem MPI jest duże. Rozkłady wielkości mają charakter bimodalny z dużymi wartościami w fazie nukleacji. Wtedy istotny jest pomiar liczby cząstek stałych o średnicy mniejszej niż 10 nm. Emisja z pojazdu z wtryskiem typu DI nie wykazuje typowego jednolitego kształtu rozkładu wymiarowego, również liczba cząstek stałych jest mniejsza niż z pojazdu starszego. Nie zauważono znaczącej emisji cząstek w fazie nukleacji, a stężenia cząstek najmniejszych o średnicy poniżej 10 nm są nieznaczne. Pobór próbki spalin przy zastosowaniu dużego współczynnika rozcieńczenia ma zauważalny wpływ na zwiększenie stężenia cząstek stałych.

2

Improvement of air quality in vehicle cabins by nanoparticle filtration

Burtscher H., Mayer A., Loretz S., Keller A., Kasper M., Czerwinski J.

Journal of KONES

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2010

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Vol. 17, No. 4

79-88

EN

A filter system is presented which allows the reduction of the concentration of ultrafine particles in vehicle cabins to very low levels. The original ventilation system is switched to the recirculation mode and all cabin intake air is supplied via a retrofitted filter system. Tests with a variety of different vehicles (from passenger cars to coaches) show the efficiency of the system. Filters incorporated in present ventilation systems remove large particles, for example pollen, but usually are inefficient for removing very small particles. This is demonstrated by Fig. l, where the particle number concentration outside and inside a car is plotted during a journey near Zurich. It is obvious that the concentrations inside and outside are more or less identical. All windows were closed during this measurement. Tests with a number ofdifferent all cars showed similar results. The filters included in today 's ventilation systems usually cannot remove nanoparticles, and so vehicle cabin indoor and outdoor nanoparticle concentrations are more or less identical. The nanocleaner, consisting of a very effident filter and a high performance blower, allows reduction of the particle concentration in the cabin from several hundreds of thousands or millions per cc. to a few thousand per cc., equivalent to remote woodland, the total exposed dose being reduced by some two orders of magnitude.

3

Air quality filtration in vehicle cabins

Burtscher H., Mayer A., Loretz S., Keller A., Kasper M., Czerwinski J.

Journal of KONES

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2009

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Vol. 16, No. 2

59-69

EN

A filter system is presented which allows the reduction of the concentration of ultrafine particles in vehicle cabins to very low levels. The original ventilation system is switched to the recirculation mode and all cabin intake air is supplied via a retro fitted filter system. Tests with a variety of different vehicles (from passenger cars to coaches) show the efficiency of the system. Number concentration of particles inside and outside a car, the nanoparticle filtration system, fllter-efficiency: transmission for the new filter and for the filter loaded to apressure drop of 2.9 mbar, setup of the filter with integrated prefilter for course particles and blower, prototype of the filter system, main filter, prefilter and blower are included the system operated by an external control box, containing the drive electronics for the blower and displays for filter pressure drop and time meter, filter pressure drop as function of operating time in a highly polluted road tunnel, a possible solution to mount the filter system, particle concentration inside and outside the car (passenger car), concentration drops to very low levels, particle concentration inside and outside a passenger car with the filter turned on, two nanocleaner filter systems mounted in a school bus, filter system for buses installed in the luggage compartment are presented in the paper.