particle emissions from vehicles : feedback of road transport...oct 01, 2014 · 2013 -elles 3...
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Renewable energies | Eco-friendly production | Innovative transport | Eco-efficient processes | Sustainable resources
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Forum AE – WP3 1st Meeting 10/01/2014 - Manchester
Ludovic Noël
Research engineer , Fuel, Emissions & Lubricants department
Olivier Colin
Research engineer , Engine CFD & Simulation department
Christian Angelberger
Project Leader, Engine CFD & Simulation department
Particle emissions from vehicles : Feedback of road transport
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Outline
Context
Evolution of EU emission regulations for road transport
Description of particles emitted by vehicles
Detailed characterization of particles
Solutions to reduce particle emissions
CFD modeling at IFPEN
Conclusions
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Context
Historically, particle emissions have been related
to Diesel vehicles and to road transport
Due to their demonstrated relationship with health
effects, a lot of research studies have been
performed to reduce emissions from Diesel
engines
Comprehension of formation mechanisms
Development of technical solutions
Useful experience to reduce other sources of
particles
Other vehicle technologies
Air transport…
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Context
Air quality standards in Europe aims to reduce population exposure to air
pollutants
PM10, PM2.5, NO2, CO, O3...
The Member States should propose an air quality plan to ensure compliance with the
limit values
Role of transports
Emissions from transport
have been declining since 1990,
but Transport remains an important
source for NOx and PM emissions
In 2010, the daily limit value for PM10
was exceeded at 33 % of traffic sites
across the EU source : European Environment Agency
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Road transport Evolution of PM emission regulations in Europe
Strong reduction of PM emissions
from Diesel engines during the last
20 years
Euro5&6 PM limit = 4,5 mg/km on
NEDC
On Board Diagnostics (OBD) limit for
Euro6 : 12 mg/km
1 “Euro1 new Diesel vehicle” ~ 30
“Euro5” Diesel vehicles for PM
emissions ...
... probably more by taking into
account the ageing of vehicles
(drifting of nominal emissions)
Euro1
1993Euro2
1996Euro3
2000Euro4
2005Euro5
2011Euro6
2014
S1
0
0,05
0,1
0,15
PM
(g
/km
)
Evolution of EU emission regulations for Light Duty vehicles
-96%
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EuroI
1992EuroII
1998EuroIII
2000EuroIV
2005EuroV
2008Euro VI
2013
Steady state testing
Transient Testing0
0,05
0,1
0,15
0,2
0,25
0,3
0,35
0,4
PM
(g
/kW
h)
Evolution of EU emission regulations for Heavy Duty engines
-97%
Road transport Evolution of PM emission regulations in Europe
StageI
1999StageII
2002 StageIIIA
2006StageIIIB
2011StageIV
2014
130-560kW
75-130kW
37-75kW19-37kW
0
0,2
0,4
0,6
0,8
1
PM
(g
/kW
h)
Evolution of EU emission regulations for Non Road engines
-95%
Simultaneously, PM emissions from
new types of heavy duty engines have
been also strongly decreased
Emission durability period extended
(€VI : 700000 km or 7 years for the last
class of vehicles)
From Euro IV, OBD required
Euro VI regulation introduced off-cycle
emissions (OCE) testing requirements
Off-Road Diesel engines
Drilling rigs, Compressors, Bulldozers,
Non-road trucks, Mobile cranes...
Emission standards are following the
same trend as for HD engines
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Road transport Evolution of PM emission regulations in Europe
Health effects related to ultrafine particles have led to further evolution of particle
emission regulations
Ultrafine particles have a low contribution to the total particle mass, but mainly affect
the total particle number
Additionally to the regulation of particle mass, a regulation of particle number has
been introduced (particle size >23nm)
Since 2011 for LD Diesel engines (6.1011 #/km, PMP measurement procedure)
From 2013 for HD Diesel engines
Off-road engines in 2017?
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Road transport Evolution of PM emission regulations in Europe
What about spark ignition (SI) engines ?
Spark Ignition Direct Injection (or
GDI) engines can emit a high
number of fine particles, sometimes
higher than Diesel equipped with
DPF
A PN emission limit for GDI vehicles has
been defined in 2 steps
6.1012 #/km from 2014
6.1011 #/km (= Diesel limit) from 2017
Towards a “fuel neutral” regulation for
particle emissions
Euro6 PN limit
source : J.Anderson et al., 2007
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Comparison of LD vehicle technologies NEDC cycle
Using a particle filter on Diesel engine leads to
a strong reduction of both particle mass and
particle number (PMP procedure)
Typical values for particle concentration are
around 1E5 #/cm3
The GDI vehicle does not comply with future
Euro6b standards for particle number
source : IFP Energies nouvelles, 2010
0
5
10
15
20
25
30
35
Diesel Euro3 Diesel + DPF Euro4 GDI Euro5
Part
icle
mass (
mg
/km
)
New European Driving Cycle (NEDC)
Euro 6 limit : 4.5mg/km
1.00E+09
1.00E+10
1.00E+11
1.00E+12
1.00E+13
1.00E+14
Diesel Euro3 Diesel + DPF Euro4 GDI Euro5
Pa
rtic
le n
um
be
r (#
/km
)
NEDC froid
Euro 6b limit (2017) : 6E11 #/km
Euro 6a limit (2014) : 6E12 #/km
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Particle emissions from vehicles From primary particles to PM 1, 2.5, 10
Primary particle (1nm-30nm) : Black
Carbon or Soot, +metals, ash ...
Aggregates of primary particles and
soluble species (50nm-1µm)
Soluble Organic Fraction : condensed
HC (PAH, Oxygenated...), Sulfates and
Water
source : Johnson et al., 1994
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Particle emissions from vehicles From primary particles to PM 1, 2.5, 10
The size distribution of particles
emitted by internal combustion
engine is bimodal
Nucleation mode (10-30nm) : poor
contribution to the total mass, but up
to 90% of the total number
Accumulation mode (50nm-1µm) :
High contribution to the total mass
Soot aggregates emitted by engines
and vehicles undergo chemical and
physical transformations into the
atmosphere and contribute to PM1,
PM2,5 or PM10 global
concentrations
source : D.B.Kittelson., 1998
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Detailed characterization
The strong evolution of emission
regulations requires a detailed
characterization of physical and
chemical properties of particles
The morphology can be analyzed
using electronic microscopy (SEM
and TEM)
Chemical analysis of the soluble
organic fraction can be performed
using High Performance Liquid
Chromatography (HPLC) :
Identification of 15 polycyclic
aromatic hydrocarbons (PAH)
specified by the Environment
Protection Agency (EPA)
GC-MS, Raman Spectroscopy …
source : IFP Energies nouvelles, 2012
Diesel engine GDI engine
NEDC
source : IFP Energies nouvelles, 2013
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Soot Formation in Diesel engines
Combustion in Diesel engines is fully
heterogeneous Fuel and air are non
premixed before combustion
Strong heterogeneities of temperature and
local equivalence ratio (~fuel/air ratio)
Soot is formed into the flame between 1500
and 2000 K for rich conditions
Advanced combustion concepts allow
reducing both soot and NOx formation
High injection pressure (> 2000 bars)
Low Temperature Combustion (LTC)
Homogeneous Combustion (HCCI)
...
source : J.E.Dec., 2009
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Identification of reduction solutions Engine technology
Fuel injection system
Direct injection
High injection pressure
Multiple injections
Injector design (nozzle, holes...)
Air management
Intake manifolds
in-cylinder aerodynamics
Combustion chamber
Piston geometry
Variable Valve Actuation
Compression Ratio
Low Temperature Combustion
Electronic control ...
source : auto-innovations
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Identification of reduction solutions After treatment
Since Euro5, the low levels of PM limit requires
the use of after treatment devices, i.e. Diesel
Particle Filter (DPF) for LD vehicles
Reduction of 95-99.9% for BC,
‘’ ‘’ ‘’ 70-95% for total PM
Reduction of PN by 2 orders of magnitude
source : Andersson et al., 2001
source : IFP Energies nouvelles, 2013
1,0E+03
1,0E+04
1,0E+05
1,0E+06
1,0E+07
1,0E+08
1,0E+09
1 10 100 1000
Dp (nm)
No
rmal
ize
d C
on
cen
trat
ion
dN
/dLo
dD
p (
#/cm
3)
Without DPF
With DPF
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Identification of reduction solutions Alternative fuels
Additionally to engine technology and after treatment devices, properties of
alternative fuels can be used to enhance PM reduction (mass and/or number)
Volatility Evaporation process and mixture formation
Aromatic compounds PAH = soot precursors
Sulfur level Effect on nucleation process
Oxygenated alternative fuels
Fatty Acid Methyl Esters (FAME) for Diesel engines or Ethanol for SI engines
Paraffinic alternative fuels
High cetane number, near zero aromatic content, sulfur free
Hydrotreated vegetable Oils (HVO)
Synthetic fuels obtained by Fisher Tropsch Process (i.e. “XtL” fuels : Gas to Liquid
(GtL), Coal to Liquid (CtL), Biomass to Liquid (BtL))
Natural Gas
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Effects of fuel properties (GDI engine)
A reference ethanol-free gasoline has been compared to an E10 fuel (containing
10 % ethanol) and to an alkylate synthetic fuel mainly blended from paraffinic
compounds
The results show that the alkylate fuel leads to a strong reduction of particle
concentrations and to the diminution of the particle mean diameter compared to E0 and
E10
source : IFP Energies nouvelles, 2012
Pinj=80bar, nominal SOI
0E+00
1E+06
2E+06
3E+06
4E+06
5E+06
6E+06
7E+06
1 10 100 1000
Dp (nm)
No
rma
lize
d c
on
ce
ntr
ati
on
dN
/dL
og
Dp
(#
/cm
3)
E0E10Alkylate
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Soot formation models for Diesel applications have been developed for many
years
New chalenges for industrial applications require an evolution of CFD modeling
Model for particle size and number => sectional soot model (SSM)
Wide range of thermodynamic conditions
Effect of fuel composition (biofuels) => need for detailled chemistry in the
model => tabulated chemistry
Modelling strategy employed
SSM based on [1,2]
Coupling of SSM with the tabulated Diesel combustion model VPTHC [3]
Modeling : A major issue to reduce particle emissions
[2] Vervisch-Kljakic P., PhD thesis, IFPEN, 2012
[3] Michel J-B, Colin O., Int. Journal of Eng. Research, 2013
[1] Netzell K. et al., P. Comb. Inst., 2007
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Experimental setup
Single cylinder Diesel engine (500cc)
Particle size distribution measured with DMS 500
Commercial Diesel fuel and surrogate fuel (70% n-decane / 30% alpha-
methylnaphtalene) : good match in terms of soot emissions
Color Red Green Bleue
Rpm 2200 2200 4000
PMI [bar] 8 8 20
Fref 0,45 0,45 0,85
Variation Pinj EGR Richesse
(tinj)
CFD modeling Evaluation on an Diesel engine Database
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RANS simulations
IFP-C3D code
Combustion: VPTHC
Soot: SSM
Surrogate chemistry from Reaction
Design consortium (590 species, 3894
reactions)
Quantitative agreement for a majority
of points with SSM
Peak position and width of SNDF is
correctly recovered
Mass flow rate
CFD modeling RANS Simulations
Size distribution
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Soot size distribution averaged over the combustion
chamber. Reference case at 4000 rpm
Reference case at 4000rpm
time= 30 CAD ATDC
Fuel/air ratio (up left)
Temperature (up right)
Soot mass fraction in
sections:
1nm (down left)
20nm (down right)
CFD modeling Space and time evolutions
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Conclusions
The knowledge from road transport and Diesel particles can be useful to reduce
particle emissions from other sources
Comprehension of formation mechanisms
Measurement procedures, Analysis
Reduction pathways
Particle emissions emitted by road transport have been strongly reduced during
the last 20 years
Reduction of the particle mass by a factor of ~30
Limitation of ultrafine particles (particle number)
The combination of different technical solutions allowed reducing particle
emissions from road transport
Optimization of the combustion process
Development of alternative fuels
After treatment devices
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Conclusions
Research activities are now focusing on the characterization of ultrafine particles
emitted by vehicles
Comprehension of the formation mechanisms of soot particles in SI engines
Impact of DPF regeneration processes on the emission of ultrafine particles
Improvement of prediction models ASMAPE project : Advanced Soot Model for Aeronautics and Piston Engines (IFPEN, SNECMA, PSA, CORIA,
CNRS)
Requirement of an accurate characterization of the nature of nanoparticles (<50nm)
from combustion processes
Chemical composition
Morphology
Identification of sources and comprehension of evolution process
Remaining questions
What is the relationship between ultrafine particles emitted by vehicles (0-100nm) and
PM10 ? Evolution of atmospheric aerosols
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