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Directive 2005/55/EC of the European Parliament and of the Council of 28 September 2005 on the approximation of the laws of the Member States relating to the measures to be taken against the emission of gaseous and particulate pollutants from compression-ignition engines for use in vehicles, and the emission of gaseous pollutants from positive-ignition engines fuelled with natural gas or liquefied petroleum gas for use in vehicles (Text with EEA relevance) (repealed)
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This is the original version (as it was originally adopted).
For the evaluation of the gaseous emissions, the chart reading of the last 30 seconds of each mode shall be averaged, and the average concentrations (conc) of HC, CO and NOx during each mode shall be determined from the average chart readings and the corresponding calibration data. A different type of recording can be used if it ensures an equivalent data acquisition.
For the NOx check within the control area, the above requirements apply for NOx, only.
The exhaust gas flow GEXHW or the diluted exhaust gas flow GTOTW, if used optionally, shall be determined in accordance with Annex III, Appendix 4, Section 2.3.
The measured concentration shall be converted to a wet basis according to the following formulae, if not already measured on a wet basis.
For the raw exhaust gas:
and,
For the diluted exhaust gas:
or,
where:
=
g water per kg dry air
=
relative humidity of the dilution/intake air, %
=
saturation vapour pressure of the dilution/intake air, kPa
=
total barometric pressure, kPa
As the NOx emission depends on ambient air conditions, the NOx concentration shall be corrected for ambient air temperature and humidity with the factors given in the following formulae:
with:
=
0,309 GFUEL/GAIRD - 0,0266
=
- 0,209 GFUEL/GAIRD + 0,00954
=
temperature of the air, K
=
humidity of the intake air, g water per kg dry air
in which
=
relative humidity of the intake air, %
=
saturation vapour pressure of the intake air, kPa
=
total barometric pressure, kPa
The emission mass flow rates (g/h) for each mode shall be calculated as follows, assuming the exhaust gas density to be 1,293 kg/m3 at 273 K (0 C) and 101,3 kPa:
[(1)]
[(2)]
[(3)]
where NOx conc, COconc, HCconc (1) are the average concentrations (ppm) in the raw exhaust gas, as determined in Section 4.1.
If, optionally, the gaseous emissions are determined with a full flow dilution system, the following formulae shall be applied:
[(1)]
[(2)]
[(3)]
where NOx conc, COconc, HCconc (1) are the average background corrected concentrations (ppm) of each mode in the diluted exhaust gas, as determined in Annex III, Appendix 2, Section 4.3.1.1.
The emissions (g/kWh) shall be calculated for all individual components in the following way:
The weighting factors (WF) used in the above calculation are according to Section 2.7.1.
For the three control points selected according to Section 2.7.6, the NOx emission shall be measured and calculated according to Section 4.6.1 and also determined by interpolation from the modes of the test cycle closest to the respective control point according to Section 4.6.2. The measured values are then compared to the interpolated values according to Section 4.6.3.
The NOx emission for each of the control points (Z) shall be calculated as follows:
The NOx emission for each of the control points shall be interpolated from the four closest modes of the test cycle that envelop the selected control point Z as shown in Figure 4. For these modes (R, S, T, U), the following definitions apply:
=
Speed(T) = nRT
=
Speed(U) = nSU
=
Per cent load(S)
=
Per cent load(U).
The NOx emission of the selected control point Z shall be calculated as follows:
and:
where,
=
specific NOx emission of the enveloping modes calculated in accordance with Section 4.6.1.
=
engine torque of the enveloping modes
The measured specific NOx emission of the control point Z (NOx,Z) is compared to the interpolated value (EZ) as follows:
Based on C1 equivalent.
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