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

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Figure 1.3 Calculating emissions from road traffic, emissions of VOC and PAH components<br />

caused by combustion of motor fuels<br />

EMISSION VOC<br />

per<br />

per<br />

- vehicle category<br />

- fuel type<br />

- road type<br />

mln kg<br />

EMISSIONS mln kg<br />

- year of manufacture<br />

- vehicle category<br />

- fuel type<br />

- road type<br />

PROFILE of<br />

VOC emission<br />

per<br />

fuel type<br />

Evaporation of motor fuels; VOC and VOC components<br />

Petrol evaporates to some extent from vehicles when they are parked, when they cool off after<br />

travelling and while they are travelling. In the Netherlands the evaporative emissions are calculated<br />

according to the methodology <strong>de</strong>scribed in the European ‘Emission Inventory Gui<strong>de</strong>book 2007’ [Ref.<br />

116: EEA, 2007]. This methodology distinguishes three mechanisms which are primarily responsible for<br />

the evaporative emissions from petrol driven vehicles (in case of LPG, diurnal emissions only):<br />

1. Diurnal emissions<br />

Diurnal emissions are evaporative emissions caused by a daily variation in the out<strong>door</strong> air<br />

temperature. A rise in temperature will cause an increase of the amount of petrol vapour in the fuel<br />

system (tank, fuel pipes and fuel injection system). A part of this vapour is emitted (together with<br />

air) from the system to prevent overpressure (tank breathing). Diurnal emission mainly originate<br />

from the fuel tank and are not <strong>de</strong>pen<strong>de</strong>nt on vehicle use. The amount of diurnal emissions is<br />

expressed in grams per vehicle per day.<br />

2. Running losses<br />

The running losses are evaporative emissions which occur while driving. The heat of the engine<br />

leads to warming up of the fuel in the fuel system and by that to evaporation of a fraction of the fuel.<br />

In mo<strong>de</strong>rn cars the extent of use has no influence on the fuel temperature in the tank. Due to this the<br />

running loses (and also hot and warm soak emissions) of these cars are very low. Running loses are<br />

expressed in grams per car kilometre.<br />

3. Hot and warm soak emissions<br />

Hot and warm soak evaporative emissions are also caused by the engine heat and occur when a<br />

warm engine is turned off. The difference between hot soak and warm soak emissions is related to<br />

the engine temperature: hot soak occurs when the engine is completely warmed up. The<br />

evaporation of petrol is less when the engine is not yet entirely warmed up. This is this case with<br />

warm soak. Hot and warm soak emissions are expressed in grams per vehicle per stop.<br />

The amount of petrol vapour released from these three mechanisms strongly <strong>de</strong>pends on out<strong>door</strong><br />

temperature (variations), the fuel volatility and the type of fuel injection. Furthermore running losses<br />

<strong>de</strong>pend on vehicle use. Due to the application of carbon cannisters in new cars since the early<br />

nineties the evaporative emissions have been reduced strongly. These cannisters adsorb the majority<br />

of the emitted petrol vapour and lead this back into the engine.<br />

The Emission Inventory Gui<strong>de</strong> Book inclu<strong>de</strong>s a generic set of emission factors for each of the<br />

mechanisms mentioned above. Within these sets a distinction is ma<strong>de</strong> into the cannister type, cylin<strong>de</strong>r<br />

capacity, and average out<strong>door</strong> temperatures. Each set contains separate emission factors for cars<br />

with a carburator and cars with fuel injection. Based on these factors a set of basic emission factors<br />

19

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