Abstract
The usage of natural gas (NG) engines is expected to
increase in coming years due to the increased
availability, competitive cost and lower CO2 emissions
compared to conventional liquid fossil fuels. However, NG
engines can produce emissions that can have impact on
environment and human health. The major hydrocarbon
species emitted by NG engines is methane and another
important emission component found in NG engines
emissions is formaldehyde. Particle emissions from NG
engines are known to be low compared to conventional
diesel engines, because of lower soot particle formation
in combustion, but particle number emissions of NG
engines, especially nanoparticle emissions, are not
necessarily low. In order to diminish the environmental
and health effects with the tightening emission
limitations the after-treatment systems are used
increasingly also with the NG engines. The aim of this
study was to examine three different catalyst systems
(oxidation catalysts and Selective Catalytic Reduction,
SCR) in the natural gas engine operating at different
conditions. The effects of catalyst systems on the
gaseous and particle emissions were investigated with the
special focus on the chemical composition of particles.
Two measurement campaigns were conducted in 2014-2015.
The test engine was a passenger car gasoline engine
modified to run with NG. The driving conditions were
selected based on the emission levels and two different
engine driving modes were used. Two catalyst setups were
tested the first one consisting of a combination of an
oxidation catalyst and a SCR and the other setup having
of only one oxidation reactor. Exhaust gas temperature
was varied from 350 to 500 °C and exhaust gas flow was
either 80 kg/h or 40 kg/h.
The chemical composition of NG emission particles was
studied by using a Soot Particle Aerosol Mass
Spectrometer (SP-AMS, Aerodyne Research Inc, Onasch et
al., 2012). In addition to the particulate chemistry,
inorganic and organic gases, particulate matter (PM) and
particle size distributions were measured by several
instruments. The volatility of particles was investigated
by using a thermodenuder and the potential of NG emission
to produce secondary particles was examined by Potential
Aerosol Mass (PAM)-chamber (Kang et al., 2007). NG
exhaust was diluted by a factor of ~10-150 depending on
the measurement devices. The particle measurements
indicated that the catalysts decreased the total PM at
all test conditions by 45-73%. However, the PM
concentrations increased as the exhaust temperature
increased. Based on the concentrations of chemical
species, the increase of mass was mostly due to the
larger concentration of sulfate and ammonium but also
hydrocarbon concentration was larger with higher exhaust
temperature. Detailed study of the mass spectra of
organics revealed that in some cases a large portion of
hydrocarbon signal was found at very small mass fragments
(e.g. CH2+, CH3+, CH4+) compared to what is typically
found in e.g. diesel fuel exhaust particles. In addition
to organic and inorganic species (sulfate, nitrate,
ammonium), the SP-AMS enabled the detection of metals in
NG emission particles. Regarding the potential of NG
emissions to form secondary aerosol, the concentration of
potential secondary organic aerosol was more than ten
times larger than the concentration of primary organic
aerosol in some engine conditions. The ratio of potential
secondary aerosol to primary aerosol was even larger for
inorganic nitrate, sulfate and ammonium. The disadvantage
of the usage of the SP-AMS in NG emission measurements is
the particle size range measured by the SP-AMS. SP-AMS
can detect particles from ~50 to 800 nm whereas the
number size distribution of NG emission particles can
peak at as small particle size as 2-5 nm (Alanen et
al.2015). The formation of secondary particles increases
the size, which can distort the comparison of primary and
secondary particles as the secondary particles as more
readily measured with the SP-AMS.
Original language | English |
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Publication status | Published - 2016 |
MoE publication type | Not Eligible |
Event | 22nd European Aerosol Conference, EAC 2016 - Tours, France Duration: 4 Sept 2016 → 9 Sept 2016 |
Conference
Conference | 22nd European Aerosol Conference, EAC 2016 |
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Abbreviated title | EAC 2016 |
Country/Territory | France |
City | Tours |
Period | 4/09/16 → 9/09/16 |