next
previous
items

Indicator Assessment

Energy efficiency and specific CO2 emissions

Indicator Assessment
Prod-ID: IND-110-en
  Also known as: TERM 027
Published 24 Jan 2013 Last modified 11 May 2021
9 min read
This is an old version, kept for reference only.

Go to latest version
Topics:
This page was archived on 10 Oct 2017 with reason: Content is outdated
  • Specific CO2 emissions of road transport have decreased since 1995, mainly due to an improvement in the fuel efficiency of passenger car transport. Recent EU Regulation setting emission performance standards for new passenger cars is expected to further reduce CO2 emissions from light-duty vehicles in view of the 130 g/km and 95 g/km emission targets set for 2015 and 2020 respectively.
  • Specific CO2 emissions of air transport, although decreasing, are of the same order of magnitude as for road, while rail and maritime shipping remain the most energy efficient modes of passenger transport.
  • Specific energy efficiency of light and heavy duty trucks has improved, but road transport still consumes significantly more energy per t-km than rail or ship freight transport. CO2 emissions from light commercial vehicles are also expected to decrease in view of the 175 g/km and 147 g/km emission targets set for 2017 and 2020 respectively.
This indicator is discontinued. No more assessments will be produced.

Specific CO2 emissions per passenger-km and per mode of transport in Europe, 1995-2011

Note: The graph shows development of specific CO2 emissions, defined as emissions of CO2 per transport unit (passenger-km), by passenger transport mode (road, rail, maritime, air) over the period 1995 to 2011. Data coverage: EEA-32 excluding Iceland and Liechtenstein

Data source:

Specific CO2 emissions per tonne-km and per mode of transport in Europe, 1995-2011

Note: The graph shows development of specific CO2 emissions, defined as emissions of CO2 per transport unit (tonne-km), by freight transport mode (road, rail, maritime, inland shipping) over the period 1995 to 2011. Data coverage: EEA-32 excluding Iceland and Liechtenstein

Data source:

Specific CO2 emissions from road passenger and freight transport in Europe, 1995, 2005 and 2011

Note: The graph shows development of specific CO2 emissions for the road transport mode, by category (passenger cars, vans, two wheelers, buses & coaches, light-duty vehicles, heavy-duty vehicles) in 1995, 2005 and 2011. Data coverage: EEA-32 excluding Iceland and Liechtenstein

Data source:

The specific CO2 emissions of the road sector were reduced between 1995 and 2011 by 7 % for passenger transport and 19 % for freight transport. The energy efficiency and CO2 per passenger-kilometre of passenger car transport has improved by almost 8 % over the same period and this improvement results partly from the voluntary agreement of the automotive manufacturing industries. The reductions in road freight transport are due to both technical improvements of the light and heavy-duty trucks (mainly in the engine efficiency) and increased activity of the heavy-duty trucks, i.e. higher load factors.

The combined effect of improvements in aircraft technology and increased load factors has resulted in a decrease in specific CO2 emissions of air passenger transport by 33 % between 1995 and 2011. However, the total emissions are still growing as a result of transport volumes growing faster than efficiency improvements.

Rail is the most energy efficient mode of passenger transport and the second most energy efficient mode of freight transport (after maritime). Specific CO2 emissions of rail transport have decreased by about 24 % from 1995 to 2011 for passenger transport, mainly due to shifting from diesel to electric trains. Passenger-kilometres of electric trains have increased by 16 %, whereas for diesel trains they decreased by 10 % over the same period. For freight transport the decrease over the same period was 40 % as a result of both technological improvements and increased load factors. The CO2 emission factors for electricity production represent the emissions incurred during the whole production and supply process from fuel extraction to electricity transport to the sub-stations feeding the railway network.

The energy efficiency of maritime shipping has only recorded slight changes of the order of 2 % in the time period considered.

Average emissions for new cars (gCO2/km) (EU-27)

Note: Graph showing progression of average emissions for new cars versus 2015 and 2020 targets

CO2 emissions from the new passenger car fleet in the EU 27 decreased from 140.2 g CO2/km in 2010 to 135.7 g CO2/km in 2011. The overall trend is one where average emissions of CO2 have decreased steadily since 2000. If similar progress is made each year, then the 2020 target for passenger cars for achieving a fleet average of 95 g CO2/km will also be achieved. However, there is also discussion regarding the real fuel consumption of vehicles, and therefore CO2 emissions. Data to monitor the average emissions of CO2 for the new van fleet are not yet available. Member States will be required to monitor and deliver this data from 2012. However, it has been estimated that average CO2 emissions for the new van fleet decreased from 203 g CO2/km in 2007 to 181 g CO2/km in 2010 (TNO et al., 2012).

Supporting information

Indicator definition

Specific CO2 emissions are defined as emissions of CO2 per transport unit (passenger-km or tonne-km), specified by mode (road, rail, inland, maritime, air).

CO2 emissions from new passengers cars are expressed in grams of CO2 per km (g CO2/km). The data, which are experimental, are measured in the vehicle type approval procedure.

Units

For passenger transport, specific CO2 emissions are expressed in g per passenger-kilometre (g/pkm).

For freight transport, specific CO2 emissions are expressed in g per tonne-kilometre (g/tkm).

For new passenger cars, tailpipe emissions are expressed in g per kilometre (g/km).


 

Policy context and targets

Context description

Since specific CO2 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. Reductions of specific emissions can be achieved by increasing occupancy rates and load factors and/or by decreasing 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).

Targets

There are no specific objectives or targets related to energy efficiency or specific CO2 emissions. Policy objectives are only set with respect to the CO2 emissions of passenger cars and light commercial vehicles. Regulation No 443/2009 specifies that each vehicle manufacturer must achieve a fleet-average CO2 emission target of 130 g/km by 2015 for all new cars registered in the EU. In order to meet the CO2 emission target of 120 g/km, additional measures, such as the use of biofuels, aim to further reduce emissions by of 10 g/km. The Regulation also defines a long-term target of 95 g/km to be reached after 2020.

The Vans Regulation No 510/2011 specifies a fleet-average CO2 emission target of 175 g/km to be phased in between 2014 and 2017 for newly registered vans in the EU. A long-term target of 147 g/km is specified for 2020.

As an additional incentive for the introduction of more energy efficient technologies (hybrid, plug-in hybrids, electric vehicles, electric vehicles with a range extender), vehicles with CO2 emissions below 50 g/km receive super-credits. For passenger cars, each such vehicle is counted as 3.5 cars in 2012 and 2013, 2.5 cars in 2014, 1.5 cars in 2015 and 1 car from 2016 onwards. For vans, each vehicle with CO2 emissions below 50 g/km is counted as 3.5 cars in 2014 and 2015, 2.5 cars in 2016, 1.5 cars in 2017, and 1 car from 2018 onwards.

Related policy documents

No related policy documents have been specified

 

Methodology

Methodology for indicator calculation

For passenger transport, specific emissions are calculated by dividing the CO2 emissions of each mode (i.e. road, rail, maritime and air transport) by the respective passenger-kilometres.

For freight transport, specific emissions are calculated by dividing the CO2 emissions of each mode (i.e. road, rail, inland shipping and maritime transport) by the respective tonne-kilometres.

For CO2 emissions from new passenger cars, data are compiled from DG-CLIMA monitoring 2000-2009, and from the EEA from 2010.

Methodology for gap filling

Passenger- and tonne-kilometres and CO2 emissions are modelled and therefore no gap filling is necessary.

Methodology references

No methodology references available.

 

Uncertainties

Methodology uncertainty

COPERT 4 is used for emissions calculations in EC4MACS. CO2 emissions are consistent with UNFCCC submissions.

Data sets uncertainty

Since the data on CO2 emissions, passenger-km and tonne-km are modelled rather than measured, the data must be treated as estimates. Data on CO2 emissions are less uncertain, as they are calibrated against statistical fuel consumption. Hence, the uncertainty of the passenger-km and tonne-km data characterises the overall uncertainty of the indicator. EC4MACS is not so accurate for calculating vehicle and tonne kilometres. This means that the overall uncertainty of passenger-km and tonne-km (as a modelled output) depends on the uncertainty of the underlying statistical data provided as input to the model. The latter may vary significantly among different countries, depending on the way data are collected and reported.

Rationale uncertainty

N/A

Data sources

Other info

DPSIR: Pressure
Typology: Descriptive indicator (Type A - What is happening to the environment and to humans?)
Indicator codes
  • TERM 027
Frequency of updates
This indicator is discontinued. No more assessments will be produced.
EEA Contact Info info@eea.europa.eu

Permalinks

Geographic coverage

Temporal coverage

Dates

Topics

Topics: