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Indicator Assessment
The specific emissions of air pollutants from passenger and freight transport decreased during the time period 1995-2006 for the majority of transport modes and especially for passenger transport. The highest reduction of specific emissions can be observed in the road sector, following the implementation of increasingly strict emission standards. Railway and maritime passenger and freight transport emissions remained approximately constant over the same time period. Rail and water transport are still relatively clean forms of transport - compared to road and air transport - but without any regulations on their emissions, these modes might lose this leading position.
For passenger transport, specific emissions are expressed in grams of pollutant (NOx, VOC, PM, CO) per passenger-kilometer.
For freight transport, specific emissions are expressed in grams of pollutant (NOx, VOC, PM, CO) per tonne-kilometer.
Since specific emissions are expressed per transport unit, occupancy rates and load factors have a considerable effect on specific emissions produced from passenger and freight transport respectively. Reduction of specific emissions can be achieved by increasing occupancy rates and load factors and/or by decreasing the emissions per vehicle-km (e.g. by setting stricter emission standards and introducing more energy efficient technologies such as hybrid, plug-in hybrids, electric vehicles, etc).
No explicit targets exist at European level directly addressing specific emissions. Policy objectives are rather set with respect to the environmental performance of the fleet (see also TERM 34).
No related policy documents have been specified
For passenger transport, the specific emissions are calculated by dividing the pollutant emissions of each mode (i.e. road, rail, maritime and air transport) by the respective passenger-kilometres.
For freight transport, the specific emissions are calculated by dividing the pollutant emissions of each mode (i.e. road, rail, inland shipping and maritime transport) by the respective tonne-kilometres.
The pollutant emissions for the remaining modes of transport (i.e. rail, inland shipping, maritime and air transport) are calculated using Tier 1 emission factors from the EMEP/EEA air pollutant emission inventory guidebook.
Activity data for inland shipping rail and maritime transport are extracted from PRIMES, Eurostat.
For air transport, the number of total LTOs (from EUROSTAT-avia_tf_aca) is used to calculate the pollutant emissions.
For the calculation of emissions from electric trains, the relevant emission factor from electricity generation (in grams of pollutant per kWh of energy produced) was used. To this aim, the total emissions of each pollutant (data from the EU submission to CLRTAP), were divided by the total electricity production in the European Union (data from EUROSTAT).
Passenger- and tonne-kilometres and emissions of NOx, VOC, PM and CO are modelled and therefore no gap filling is necessary.
COPERT 4 is used for road transport emissions calculations in EC4MACS, whereas the Tier 1 method of the EMEP/EEA air pollutant emission inventory guidebook is used for non-road transport modes.
Since the data on pollutant emissions, passenger-km and tonne-km are modelled rather than measured, the data must be treated as estimates. The uncertainty of emissions and the uncertainty of passenger-km and tonne-km vary significantly among different countries depending on the underlying statistical data used for each country
No uncertainty has been specified
For references, please go to https://www.eea.europa.eu/data-and-maps/indicators/specific-air-pollutant-emissions/specific-air-pollutant-emissions-assessment or scan the QR code.
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