TECHNICAL FIELD
[0001] The present invention relates to a system and method for accurately measuring the
nitrogen oxides, i.e. NOx and ammonia i.e. NH
3 contents in exhaust fumes.
[0002] More particularly, it concerns a novel arrangement of sensors to measure NOx and
NH
3 in exhaust fumes that can be produced by combustion.
[0003] Throughout this application, the term "exhaust fumes" designates gases formed during
the combustion process for example in vehicle engines, and include among others nitrogen
oxides (NOx) such as NO, NO
2 and the like and ammonia (NH
3).
[0004] Throughout this application, the term "sensor" designates a module that can detect
the presence and content of a particular gas and process the signal to convert said
signal into a usable data.
[0005] Throughout this application, the term "exhaust" designates a duct or a pipe through
which exhaust fumes from a combustion process are evacuated.
[0006] Throughout this application, the term "interfere" when used for a gas designates
the phenomena by which a given gas can alter the measurement of a target gas. Cross-sensitivity
is one example of interference.
[0007] Throughout this application, the term "downstream" and "upstream" are used with reference
to the exhaust evacuation outlet.
BACKGROUND ART
[0008] The ever growing desire by policy makers to reduce the emissions from vehicle engines
is followed by tougher regulations on emitted gases. Particularly, the emissions of
NOx are closely monitored by regulators as these gases were identified as pollutants.
Hence, the accurate monitoring of NOx is an important aspect.
[0009] The emissions from exhaust can be measured using different methods and instruments.
[0010] Portable emissions measurement system (PEMS) devices can give reliable NOx contents
in exhaust fumes. These devices are designed for measurement campaigns and the bulkiness
of such devices make them not suitable for long term measurements and for control
systems on vehicles.
[0011] Sensors on the other hand are commonly used for long term measurements and for engine
controls. Commercially available NOx sensors can give an accurate measurement of NOx
contents in exhaust fumes, but in some circumstances NH
3 also present in the exhaust fumes can interfere with NOx measurements. The cross-sensitivity
of NOx sensors to NH
3 can thus give false readings.
[0012] The inventors have compared the NOx contents measured by a PEMS commercialized by
SENSORS, INC. under the designation SEMTECH and by NOx and O
2 sensors under the designation EGS-NX commercialized by the BOSCH company. The measurements
were carried out on a NH
3 non-emitting vehicle.
[0013] The data collected by the PEMs and the NOx and O
2 sensors are presented on Figure 1A and 1B. The two signals are almost identical.
On the data recorded by the PEMS the signal is filtered by the long length of the
sampling line while the NOx recorded by the sensor is seen more dynamic. Nevertheless
the cumulative contents of NOx obtained with the two methods overlap almost perfectly.
If NH
3 interference is suppressed, therefore NOx sensors alone can give reliable NOx contents
measurements almost as accurate as the ones obtained with a PEMS. The robustness and
the relative lower cost of sensors are also an advantage over PEMS.
[0014] The challenge also consists to obtain accurate measurements for stoichiometric combustion
engine, because NOx and NH3 sensors are not designed to operate in such conditions.
[0015] The ECM company has already commercialized a NOx and NH
3 analyzer following this strategy. The analyzer uses two NOx sensors placed in series.
The first sensor is used to measure the combined NOx and NH
3 contents in the raw exhaust fumes i.e. untreated exhaust fumes. The second sensor
measures the NOx contents in treated exhaust fumes where the NH
3 is removed using a NH
3 scrubber. The difference between the contents measured by the first sensor and the
contents measured by the second sensor gives the NH
3 contents. One of the drawbacks of such analyzer is the fact that the NH
3 scrubber needs to be regenerated now and then, cupric sulfate is used to prepare
the scrubber solution. The system also requires a sampling pump which makes combined
with the NH
3 scrubber the analyzer bulky.
[0016] In a similar approach,
WO2016/068831 patent application discloses a system with a NH
3 oxidation catalyst layered on top of a NOx sensor. The oxidation catalyst converts
the NH
3 present in the exhaust fumes into N
2 while leaving the NOx intact, which can then be analyzed without the interference
of NH
3. One of the drawback of this system is related to the deactivation process of catalysts
on the long run, which eventually will require regeneration or replacement of the
catalyst.
[0017] There is therefore a need to improve the systems for the accurate measurement of
NOx and NH
3 contents in exhaust fumes, in particular to effectively use robust and cost effective
sensors for reliable long term measurements and control systems.
[0018] The general aim of the invention is to meet at least partially this need.
SUMMARY OF THE INVENTION
[0019] To that end, a first subject of the present invention is a system for accurately
measuring NOx and NH
3 contents in exhaust fumes including for stoichiometric combustion engines, comprising:
- an exhaust to evacuate exhaust fumes connected at its free end to an exhaust evacuation
outlet,
- at least one first sensor adapted to measure NOx and O2 contents, said first sensor being placed upstream from the exhaust evacuation outlet,
- at least one second sensor adapted to measure NOx and O2 contents, said second sensor being placed downstream from the exhaust evacuation
outlet,
- at least one third sensor adapted to measure NH3, said third sensor being placed downstream from the exhaust evacuation outlet.
[0020] Thus, the invention consists essentially in measuring NOx and O
2 contents in exhaust fumes at two locations, respectively inside the exhaust and downstream
from the exhaust evacuation outlet. NH
3 contents in the exhaust fumes are also measured downstream from the exhaust evacuation
outlet.
[0021] The NOx contents measured by the first and second sensors are actually measuring
the combined NOx and NH
3 contents because of the cross-sensitivity of the sensors to said gases.
[0022] In order to calculate the NOx contents emitted by the exhaust two approaches are
envisaged. The first approach is to subtract the NH
3 contents measured by the third sensor to the NOx contents measured by the second
sensor. This gives the NOx contents downstream from the exhaust evacuation outlet.
[0023] By using the O
2 contents measured by the first upstream sensor and the second downstream sensor,
it is possible to calculate the dilution ratio of the exhaust fumes from the exhaust
and after being evacuated through the exhaust evacuation outlet. The NOx content inside
the exhaust can then be calculated using the dilution ratio.
[0024] The second approach is to calculate first the NH
3 contents in the exhaust using the dilution ratio and the NH
3 contents measured by the third sensor. By subtracting the calculated NH
3 contents to the NOx contents measured by the first sensor the NOx contents without
the NH
3 contents can be determined.
[0025] The measured NOx and NH
3 contents can be used to monitor the performance of the combustion process for example
in vehicle engines or other combustion processes. But also to evaluate the efficiency
of a treatment process of exhaust fumes. Indeed, the measured contents can give for
example information on the performance of a three way catalytic converter.
[0026] The measured contents can also be used for control systems. The data can be transmitted
to a control unit to fine tune the different parameters for the exhaust fumes treatment
processes or the performance of a combustion process.
[0027] The collected data can be stored on a memory unit for future studies or transmitted
in real time intermittently to another location via wireless communications, which
can be a telematics system.
[0028] In an advantageous embodiment, the second and third downstream sensors are placed
in such a way that the exhaust fumes reaching said sensors are diluted with at least
one gas not interfering with the sensors. Preferably, the diluting gas is air.
[0029] In a first variant, the second and third downstream sensors are placed in a sensor
housing designed to allow exhaust fumes reach the sensors while protecting the sensors
from external factors.
[0030] Alternatively, the exhaust evacuation outlet is configured as a venturi tube having
an air inlet at the constriction. Preferably, the venturi tube has a protective hood
on the air inlet.
[0031] According to an advantageous embodiment, the system comprises a memory unit to store
collected data of NOx, NH
3 and O
2 contents. Preferably, the system comprises a transmitter to send the collected NOx,
NH
3 and O
2 data to an engine control unit or to another location by a wireless protocol. Preferably,
the transmitter is a telematics system.
[0032] In another aspect, the invention concerns an assembly comprising:
- an internal combustion engine producing exhaust fumes which are evacuated to the external
environment through an exhaust connected to said engine.
- a system according to the invention in which the exhaust is the exhaust of the engine.
[0033] In a variant, the engine of the assembly is adapted to operate on a stoichiometric
mixture of air and fuel, the fuel is preferably natural gas.
[0034] In another variant, the assembly has a three-way catalytic converter to treat the
fumes leaving the engine before reaching the exhaust.
[0035] The invention concerns also, a method for accurately measuring the NOx and NH
3 contents in exhaust fumes comprising the following steps:
- 1/ measuring the NOx and O2 contents in exhaust fumes by a at least one first upstream sensor (3) placed inside
the exhaust,
- 2/ measuring the NOx and O2 contents in the exhaust fumes by at least one second sensor and measuring the NH3 content by at least one third sensor, said second and third sensors are placed downstream
from the exhaust evacuation outlet,
- 3/ calculating the instantaneous dilution factor of O2 contents, between the first upstream sensor and the second downstream sensor,
- 4/ subtracting the NH3 content measured by the third sensor and corrected with the calculated dilution factor
to the NOx content measured by the second sensor and corrected with the calculated
dilution factor, or subtracting the NH3 content measured by the third sensor and corrected with the calculated dilution factor
to the NOx contents measured by the first sensor and corrected with the calculated
dilution factor.
[0036] The invention concerns also the use of a system according to the invention for control
systems of a combustion process or an exhaust treatment process.
[0037] In another aspect, the invention concerns a vehicle comprising a system according
to the invention.
[0038] The system according to the present invention can be used on exhaust fumes emanating
from the combustion of fossil fuels or any other type of combustion susceptible to
produce NH
3 and NOx or simply containing these gases.
[0039] The system can be used particularly on vehicles with an internal combustion engine
using gasoline, diesel, natural gas, biogas, synthetic fuel and multiple fuels.
BRIEF DESCRIPTION OF THE DRAWINGS
[0040] Other advantages and characteristics of the invention will emerge more clearly upon
perusal of the detailed description of exemplary embodiments of the invention given
as an illustration and not a limitation, making reference to the following figures,
in which:
- Figure 1A and 1B are graphs presenting the instantaneous and the cumulative NOx contents
measured by a NOx and O2 sensor and a PEMS analyzer for a NH3 non-emitting engine, according to the prior art;
- Figure 2 is a schematic side view of an example of a system according to the invention
for measuring NOx and NH3 in exhaust fumes;
- Figure 2A is a cross sectional view of system of Figure 2 according to A-A axis;
- Figure 3 is a schematic side view of another example of a system according to the
invention, with an exhaust having a Venturi tube at its free end;
- Figure 4 is a graph presenting the engine rpm and the speed of a vehicle during a
given trajectory, said vehicle being equipped with a system according to the invention;
- Figures 5A and 5B are graphs presenting the O2 contents measured by the first sensor upstream from the exhaust evacuation outlet
and by the second sensor downstream from the exhaust evacuation outlet, and the calculated
dilution ratio;
- Figure 6A to 6D are graphs presenting the instantaneous and the cumulative NOx contents
measured by the first and second sensors corrected by the dilution ratio;
- Figures 7A and 7B are graphs presenting the NOx contents measured by the second downstream
sensor and a PEMS analyzer, and the NH3 contents measured by the third sensor downstream sensor;
- Figure 8 is a graph presenting the cumulative NOx contents as measured by the second
downstream sensor and the PEMS and the contents of NOx subtracted of the NH3 contents measured by the third downstream sensor, the contents measured by the downstream
sensors are corrected by the dilution ratio.
[0041] For clarity reasons, the same elements of a NOx and NH
3 measurement system will have the same the numeral references.
DETAILED DESCRIPTION OF THE INVENTION
[0042] Other advantages and features of the invention will become more apparent upon reading
the detailed description of exemplary implementations of the invention, given as illustrative
and non-limiting examples with reference to the figures.
[0043] The NOx formation from combustion involves multiple step reactions and depend on
the temperature range, the stoichiometric ratio (air to fuel) and the nitrous species
present in the combustion zone.
[0044] There are basically three recognized mechanisms for NOx formation: thermal, fuel
and prompt.
[0045] Thermal NOx is formed when atmospheric oxygen and nitrogen react at elevated temperatures.
[0046] Fuel NOx is formed when a fuel containing organically bound nitrogen reacts with
oxygen.
[0047] Finally, prompt NOx is formed when hydrocarbon radicals react with atmospheric nitrogen
to produce HCN and is oxidized to NOx.
[0048] In order to reduce the emission of NOx in exhaust fumes nowadays vehicles are equipped
with systems to either convert or trap NOx gases.
[0049] For example for gasoline and natural gas fueled vehicles a three way catalyst (TWC)
is used to simultaneously convert NOx, unburned hydrocarbons and carbon monoxide (CO)
into less harmful gases. Under slightly lean operation the three way catalyst oxidizes
hydrocarbons (HC) and CO and under slightly rich environment NOx species are reduced.
[0050] But, in some cases, operating under rich conditions favors a water gas shift and
a steam reforming reactions that form hydrogen according to the following reaction
paths:
CO + H
2O → CO
2 + H
2
HC + H
2O → CO
2 + H
2
2NO + 5H
2 → 2 NH
3 + 2H
2O
2NO + 2CO + 3H
2 → 2NH
3 + 2CO
2
[0051] The hydrogen molecules can further react with NOx and CO to form NH
3. This kind of emission was observed in diesel and natural gas engines.
[0052] For diesel fueled vehicles additional treatments can be used to reduce efficiently
NOx contents. To this end Selective Catalytic Reduction (SCR) systems were suggested
as viable technology and are already integrated in diesel vehicles. Systems implementing
the SCR technology use NH
3 as the reducing agent to convert NOx with a dedicated catalyst. A urea solution can
be used to generate the NH
3 when decomposed. In order for the SCR system to perform efficiently the right amount
of NH
3 must be injected, but the injected amount of NH
3 must also be monitored to prevent over-dosing the SCR system and causing the emission
of NH
3 to the atmosphere (referred to as NH
3-slip).
[0053] When a three way catalyst is used, the system according to this invention can give
reliable NOx and NH
3 measurements. Using this information an engine control unit (ECN) or other control
units can fine tune the exhaust fumes treatment process.
[0054] In the case where a SRC system is used, the system according to the present invention
can be used to adapt the amount of NH
3 injected in the system for efficient conversion of NOx gases without NH
3-slip.
[0055] Figure 2 shows a system 1 for the measurement of NOx and NH
3 in exhaust fumes embodying the principle of the present invention.
[0056] The system 1 according to the invention comprises an exhaust 2 adapted to evacuate
exhaust fumes 52 produced by the combustion of a fuel.
[0057] At its free end the exhaust 2 has an exhaust evacuation outlet 4 for the evacuation
of exhaust fumes to the ambient atmosphere.
[0058] At least one first sensor 3, adapted to measure NOx and O
2 contents, is installed upstream from the exhaust outlet 4. The first sensor 3 can
be a unique sensor capable of measuring NOx and O
2 at the same time or includes two separate sensors one dedicated to NOx measurements
and another one dedicated to O
2 measurements.
[0059] Before reaching the sensors housing 7 which is installed downstream from the exhaust
evacuation outlet, the exhaust fumes 52 come into contact in the zone 5 with a diluting
gas 51. This diluting gas must not interfere with the NOx and NH
3 measurements. In a particular embodiment, the diluting gas can be air. The sensor
housing 7 is designed to allow exhaust fumes reach the sensors while protecting the
sensors from external factors.
[0060] Inside the sensor housing 7, downstream from the exhaust evacuation outlet 4, a pair
of sensors 6 is installed to measure the NOx, O
2 and NH
3 contents.
[0061] As illustrated in figure 2A, the pair of sensors 6 inside the sensor housing 7 includes
two sensors 61, 62, each separately dedicated for NOx and O
2 and for NH
3 measurements. More particularly, the sensor for NOx and O
2 contents measurement is referred to as the second sensor 61 and the sensor for NH
3 contents measurements is referred to as the third sensor 62. The two sensors are
preferably placed at an equal distance from the exhaust evacuation outlet.
[0062] In another embodiment illustrated on figure 3, the exhaust 2 has at its free end
a venturi tube 8 with a diluting gas inlet 9 at the constriction of the venturi tube.
Indeed, the diluting gas is introduced in the exhaust by suction caused by the venturi
effect. Preferably, the venturi tube 8 has a protective hood 100 on the air inlet
which allows to protect from the external environment, and hence to the external conditions,
notably humidity, rain...
[0063] The exhaust fumes 52 can thus be diluted in the zone 5 with a diluting gas 51 before
reaching the sensor 6 installed downstream from the venturi tube.
[0064] In a particular embodiment the diluting gas can be air. Similarly as in the previous
embodiment the sensor 6 can be two sensors, each separately dedicated for NOx and
O
2 and for NH
3 measurements. Also, a first sensor 3 adapted to measure NOx and O
2 contents is installed upstream from the venturi tube 8.
Example
[0065] The following example illustrates how the system according to the present invention
can be implemented on a vehicle.
[0066] In this example, the measurements presented here were recorded on a vehicle with
a truck trailer of 18 tons loading equipped with a 9 liter natural gas engine.
[0067] The composition of the natural gas used in the vehicle for the measurements of emissions
is presented on Table 1. Methane is the main component of the gas used with a molar
percentage of 90.594. The natural gas used also contains ethane and other alkanes,
generally the measured concentrations of the different components of the natural gas
are within a range of commonly used natural gases.
[0068] Other characteristics such as the carbon to hydrogen ratio (C/H), the molecular weight
and the density also remain within a range of commonly used natural gases.
Table 1
| Component |
Molar % |
| N2 |
2.632 |
| CH4 |
90.594 |
| CO2 |
1.214 |
| C2H6 |
4.685 |
| C3H8 |
0.542 |
| iC4 |
0.230 |
| nC4 |
0.089 |
| neoC5 |
0.003 |
| iC5 |
0.043 |
| nC5 |
0.021 |
| C6 |
0.005 |
| Total |
100.058 |
| C/H |
3.938 |
| Molecular weight |
17.681 g/mol |
| Density |
0.791 kg/m3 |
[0069] The composition the natural gas used is assumed to be stable during the measurement
campaign.
[0070] The engine is operating with stoichiometric air-fuel mixture without Enhanced Gas
Recovery (EGR) and is equipped with a three way catalytic converter to treat exhaust
fumes.
[0071] The Air-fuel ratio also referred to as AFR defines the ratio between the mass of
air and the mass of fuel. The air-fuel ratio will have an impact on the energy released
and the extent of the combustion. Indeed, depending on the amount of air the combustion
reaction can be total, partial or none.
[0072] A complete combustion occurs when all the fuel is burned and there is no unburned
fuel in the exhaust fumes. This ideal combustion is also called stoichiometric air
to fuel ratio. For example, the stoichiometric air to fuel ratio for a combustion
with natural gas is an AFR of 17: 1. In other words, 17.2 kg of air is needed for
the total combustion of 1 kg of natural gas. The value of the coefficient λ (lambda)
defines the ratio of actual AFR to stoichiometry for a given mixture. For the given
example when the AFR ratio is equal to 16.97:1, the λ equals to 1.
[0073] Since the engine for this example is operating with a stoichiometric AFR ratio, the
λ equals to 1.
[0074] On the exhaust a first sensor 3 adapted to measure NOx and O
2 contents is installed upstream from the exhaust evacuation outlet. In the example,
the sensor is one commercialized by the BOSCH company under the designation EGS-NX.
[0075] The sensor is in contact with exhaust fumes produced by the internal combustion of
natural gas and treated by a three way catalytic converter.
[0076] A second sensor 61 adapted to measure NOx and O
2 contents is installed downstream from the exhaust evacuation outlet and finally a
third sensor 62 adapted to measure NH
3 contents is also installed downstream from the exhaust evacuation outlet. The distance
between the upstream and downstream sensors is one meter, the dephasing is assumed
to be negligible.
[0077] The second and the third sensors are placed in such a way that the exhaust fumes
reaching them is diluted with the ambient air, such as shown on figures 2 and 2A.
[0078] In order to control the NOx contents measured by the sensors a sampler with a flow
meter is installed in the exhaust fume and is connected to a PEMS under the designation
SEMTECH commercialized by SENSORS, INC.
[0079] The measurements recorded by the PEMS are assumed to be the accurate measurements
of NOx contents in the exhaust fumes.
[0080] Figure 4 presents the engine rpm and the speed of the vehicle during the measurements.
It was previously noticed that the highest NH
3 emissions were recorded when the engine was operating at a stabilized regime for
example on highways.
[0081] In order to have measurements on different regimes, during the test a route with
different driving speed was chosen. The different measurements were rephased using
the engine rpm measurements.
[0082] The O
2 contents measured by the first and the second sensors are presented on figure 5A,
this data is used to calculate the dilution ratio of the exhaust fumes by the ambient
air between the first sensor and the second sensor. The following formula was used
to calculate the dilution ratio:

[0083] In this ratio, the number 21 represents the ratio of oxygen in natural air (vol%).
[0084] The calculated dilution ratio is presented on figure 5B, the values remain below
50% and rarely goes below 2%.
[0085] Using this dilution ratio, the NOx contents measured by the second sensor were compared
to the NOx contents measured by the first sensor.
[0086] The contents measured by the first and second sensors actually measured the NOx content
and the NH
3 which might be present in the exhaust fumes.
[0087] The comparison of the contents are presented on figures 6A to 6C. The contents recorded
by the first sensor saturated at 3000 ppm which is obvious since the sensor used is
designed to accurately measure NOx levels between 0 ppm and 1650 ppm. Nevertheless,
the trend of curves recorded by the two sensors are almost identical for NOx levels
below 3000 ppm.
[0088] The cumulative NOx contents measured by the first and the second sensor are presented
on figure 6D. The difference observed between the two curves is explained by the saturation
of the first sensor for NOx contents above 3000 ppm but the trends are identical.
[0089] The comparison of the NOx contents measured by the first and the second sensor proves
that the calculation of the dilution ratio using the O
2 contents from the first and the second sensor is a satisfactory approach.
[0090] Now referring to figures 7A and 7B, the data collected for NOx contents by the second
sensor and by the PEMS and the data collected for NH
3 contents by the third sensor are compared.
[0091] Generally speaking, the trends of NOx contents measured by the second sensor and
the PEMS are quite similar, however some signals detected by the second sensor are
not detected by the PEMS, these signals are NH
3 detected by the NOx sensor.
[0092] This is confirmed by the signals observed by the third sensor measuring NH
3 contents. For example, at around 1560s and 1850s the signal observed on the NOx contents
measured by the second sensor and the signal observed on the NH
3 curve overlap, these peaks are the contribution of NH
3.
[0093] On figure 8, different cumulative NOx contents are presented. The cumulative NOx
contents are measured by the second sensor is distinctly different from the cumulative
NOx contents measured by the PEMS. Indeed, the cumulative NOx contents measured by
the second sensor has the NH
3 contribution. By subtracting the cumulative NH
3 contents to the cumulative NOx contents measured by the second a curve which overlaps
the NOx contents measured by the PEMS is obtained. This example illustrates how this
invention can be implemented on a vehicle and how reliable NOx and NH
3 contents can be measured using sensors.
[0094] The invention has been shown and described with respect to certain aspects, example,
and embodiments. While a particular feature of the invention may have been disclosed
with respect to only one of several aspects, example, or embodiments, the feature
may be combined with one or more other features of the other aspects, example, or
embodiments as may be advantageous for any given or particular application.
1. A system (1) for accurately measuring NOx and NH
3 contents in exhaust fumes, including for stoichiometric combustion engines, comprising:
- an exhaust (2) to evacuate exhaust fumes connected at its free end to an exhaust
evacuation outlet (4),
- at least one first sensor (3) adapted to measure NOx and O2 contents, said first sensor being placed upstream from the exhaust evacuation outlet,
- at least one second sensor (61) adapted to measure NOx and O2 contents, said second sensor being placed downstream from the exhaust evacuation
outlet and,
- at least one third sensor (62) adapted to measure NH3, said third sensor being placed downstream from the exhaust evacuation outlet.
2. A system according to claim 1, the second and third downstream sensors being placed
in such a way that the exhaust fumes reaching said sensors are diluted with at least
one gas not interfering with the sensors.
3. A system according to claim 2, the diluting gas being air.
4. A system according to one of the preceding claims, the second and third downstream
sensors being placed in a sensor housing designed to allow exhaust fumes reach the
sensors while protecting the sensors from external factors.
5. A system according to claim 1 to 3, the exhaust evacuation outlet being configured
as a venturi tube (8) having an air inlet (9) at the constriction.
6. A system according to claim 5, the venturi tube having a protective hood (10) on the
air inlet.
7. A system according to one of the preceding claims, comprising a memory unit to store
collected data of NOx, NH3 and O2 contents.
8. A system according to claim 7, comprising a transmitter to send the collected NOx,
NH3 and O2 data to an engine control unit or to another location by a wireless protocol.
9. A system according to claim 8, the transmitter being a telematics system.
10. An assembly comprising:
- an internal combustion engine producing exhaust fumes which are evacuated to the
external environment through an exhaust connected to said engine.
- a system according to one of the preceding claims, in which exhaust (2) is the exhaust
of the engine.
11. An assembly according to claim 10, the engine being adapted to operate on a stoichiometric
mixture of air and fuel, fuel being preferably natural gas.
12. An assembly according to claims 10 or 11, having a three-way catalytic converter to
treat the fumes leaving the engine before reaching the exhaust.
13. A method for accurately measuring the NOx and NH
3 contents in exhaust fumes comprising the following steps:
1/ measuring the NOx and O2 contents in exhaust fumes by a at least one first upstream sensor (3) placed inside
the exhaust,
2/ measuring the NOx and O2 contents in the exhaust fumes by at least one second sensor and measuring the NH3 content by at least one third sensor, said second and third sensors are placed downstream
from the exhaust evacuation outlet,
3/ calculating the instantaneous dilution factor of O2 contents, between the first upstream sensor and the second downstream sensor,
4/ subtracting the NH3 content measured by the third sensor and corrected with the calculated dilution factor
to the NOx content measured by the second sensor and corrected with the calculated
dilution factor, or subtracting the NH3 content measured by the third sensor and corrected with the calculated dilution factor
to the NOx contents measured by the first sensor and corrected with the calculated
dilution factor.
14. Use of a system according to one of claims 1 to 9 for control systems of a combustion
process or an exhaust treatment process.
15. A vehicle comprising a system according to one of claims 1 to 9 or an assembly to
one of claims 10 to 12.