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Methoden voor de berekening van de emissies door mobiele ... - CBS

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classification due to the large sample size. After 2000 the specific consumption figures have been<br />

extrapolated based on expert judgement.<br />

The fuel consumption per road type is calculated from the average consumption by using mo<strong>de</strong>l<br />

calculations for the variations in fuel consumption between travelling on various road types, and is<br />

therefore more uncertain than the average consumption.<br />

The fuel consumption by road vehicles concerns calculated figures (resulting from specific fuel<br />

consumption and vehicle kilometres) and is more uncertain than both elements separately.<br />

Fuel sales to road traffic are <strong>de</strong>termined based on a survey among fuel suppliers (oil companies) and<br />

is relatively accurate (A). These figures are used to calculate the IPCC-emissions.<br />

1.9.2 Uncertainties in emission factors (Appendix 1B)<br />

Regarding the uncertainty in the emission factors of road vehicles, a distinction can be ma<strong>de</strong><br />

according to 1) fuel-related emission factors, 2) regulated combustion and emission factors 3) nonregulated<br />

combustion and emission factors, 4) evaporative emission factors and 5) wear emission<br />

factors.<br />

Note to 1: Fuel-related emission factors are used when calculating CO2, SO2 and heavy metals. These<br />

emissions are calculated by multiplying the fuel consumption with fuel-related emission factors<br />

(grams/kg of fuel). Of these emission factors, CO2 is the most certain because this <strong>de</strong>pends only on<br />

the carbon content of the fuel, and this carbon content is relatively certain. SO2 <strong>de</strong>pends on the<br />

sulphur content, and since in recent years this has not been structurally measured, the sulphur<br />

content, especially of petrol, is very uncertain. Although the emission factors for heavy metals are<br />

based on a recent study, they are still uncertain because the content of heavy metals <strong>de</strong>pends on the<br />

composition of the refined cru<strong>de</strong> oil and the fuel additives. Both can vary strongly.<br />

Note to 2: Regulated combustion and emission factors are used for CO, VOC, NOx and in the case of<br />

diesel vehicles, for PM10 as well. Road vehicles have been subjected to emission norms for more than<br />

a <strong>de</strong>ca<strong>de</strong>; consequently, a relatively large number of measurement results are available. One example<br />

is the annual in-use compliance programme of the TNO, during which several dozen of vehicles are<br />

measured per year. The reliability of these emission factors is increased since using VERSIT+, but<br />

uncertainties still exist regarding the correction factors for the cold start, ageing and the use of air<br />

conditioners.<br />

Note to 3: Non-regulated combustion emission factors are used among other things for N2O and VOC<br />

components such as aromatics (including benzene) and PAHs. Because the profiles are from the mid-<br />

1980s and both the fuel composition and the engine technology have changed since then, the<br />

reliability of these profiles has <strong>de</strong>clined sharply. In 2002, as expected, a large-scale measurement<br />

programme was conducted to update the VOC profiles. The N2O emission factors of passenger cars<br />

have recently been ascertained as part of a comprehensive measurement study and are therefore<br />

relatively reliable (B).<br />

Note to 4: Evaporative emission factors express the quantity of evaporated petrol per vehicle per day.<br />

This <strong>de</strong>pends on the age of the vehicle, because new vehicles must comply to stricter <strong>de</strong>mands for the<br />

maximum evaporative emissions than ol<strong>de</strong>r vehicles. Moreover, the evaporative emission <strong>de</strong>pends on<br />

vehicle usage, because many short trips lead to more evaporative emissions than fewer long trips. In<br />

addition, the out<strong>door</strong> temperature is important. The evaporative emissions of road vehicles are<br />

scarcely measured in the Netherlands, and emission factors are therefore based on the emission<br />

norms and the measurement results in other European countries.<br />

Note to 5: Wear emission factors are <strong>de</strong>rived from a mass balance and assumptions about the content<br />

of particulate matter in the total wear mass. This assumption is very uncertain. The zinc content of<br />

tyres, which was modified by the traffic task group, has been recently confirmed in research conducted<br />

by BLIC, a central organization of tyre manufacturers.<br />

39

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