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Briefing
The European Union's (EU's) Seventh Environment Action Programme (7th EAP) puts forward a clear vision: 'In 2050, we live well, within the planet's ecological limits.' In order to achieve this vision, environmental pressures arising from all sectors of the economy should be significantly reduced. As it is a key economic sector, reducing the environmental, health and climate pressures arising from Europe’s transport sector is critical to achieving the 7th EAP’s longer-term objectives.
Within the EU, quantitative targets and objectives relevant to the environmental performance of the transport sector are laid out in:
Table 1 summarises the progress made for those goals that are monitored, highlighting past trends and the extent to which the EU is on track to reach respective policy targets. For each goal, a base year and corresponding value are determined, which serve as a starting point for the target trajectory. For transport GHG emissions, the 2011 Transport White Paper defined the preferred policy option to reach the objective. This forms the basis of the trajectory for reductions in transport GHG emissions. For the other objectives, a linear trend is assumed towards the target, starting from the base year. Only a selection of transport goals are provided — others cannot yet be fully monitored due to a lack of data and/or the complicated nature of the evaluation required.
Table1. Progress of the EU-28 in meeting selected transport goals.
Notes: (a) EU-28 excluding Croatia until 2013. EU-28 from 2014 onwards.
(b) Preliminary data for 2016.
(c) In the case of the Renewable Energy Directive (EU, 2009a) target, Eurostat published for the first time (2011 data) the share of biofuels in transport energy use which meet the sustainability criteria of the Directive. The large increase between 2011 and 2012 is explained by the fact that in previous years the new sustainability criteria were not fully applied. The system for certifying sustainable biofuels is increasingly operational across all Member States.
Transport emissions have increased in recent years and now account for around one quarter of the EU’s total GHG emissions (Figure 1; see also TERM 002 indicator). From 1990 to 2015, official GHG emissions from transport (including international aviation but excluding maritime shipping in line with the Transport White Paper’s 60 % reduction target), increased by 23.1 % (Table 1). The increase is more than 25 % if provisional data for 2016 reported by Member States are considered (European Environment Agency (EEA), 2017a). This increase comes despite past improvements in the efficiency of transport and is broadly in line with increases in the level of economic activity as measured by gross domestic product (GDP), as well as increases in demand for both freight and passenger transport. The transport sector remains the only major European economic sector in which GHG emissions have increased, compared with 1990 levels.
Figure 1. Evolution of greenhouse gas (GHG) emissions in the EU-28 from 1990 to 2016
Note: Preliminary data for 2016 (EEA, 2017a), although not available for international navigation.
Road transport accounts for 72.9 % of transport GHG emissions (including international aviation and maritime emissions). Emissions from the sector have grown in each of the last 3 years, mainly influenced by growth in passenger transport volumes. In 2016, emissions from road transport comprised around one fifth of the EU’s total emissions.
GHG emissions from international aviation have more than doubled since 1990 and were almost 25 % higher in 2016 than in 2000, although they still make up a relatively small share of total GHG emissions. Emissions from international aviation have increased over each of the last 4 years (2013-2016) at an average rate of around 2 % per year. As other sources of GHGs decline, emissions from aviation and shipping are increasingly significant.
Compared with the target path to meet the 2030 goals, a further reduction of 12.5 % needs to be achieved. Moreover, the long-term 2050 target requires a reduction in emissions of more than two thirds compared with 2015 levels (see Table 1).
From a peak in 2007-2008, GHG emissions from maritime ‘bunker’ fuels (i.e. fuels used in ships) sold in the EU‑28 have decreased by around one quarter, at least partly because of the subsequent economic downturn. Since 2008, there has been a downward trend, with emissions in 2015 amounting to 135 Mt CO2. This is more than 16 % below the 2005 level, from which the 2050 target is based. In order to reach the 2050 target, a further reduction of 28 % needs to be achieved.
A new system for the monitoring, reporting and verification of CO2 emissions from maritime transport (established by Regulation (EU) 2015/757) will commence in 2018. It will introduce obligations to report data on annual maritime GHG emissions and other relevant information.
Since monitoring under the current Regulation began in 2010, the annual average specific emissions from newly registered passenger cars had decreased by almost 15 % as of 2015. The 2015 target of 130 g CO2/km was already met in 2013, 2 years before the deadline. In 2016, average emissions decreased by 1.5 g CO2/km, the smallest annual decrease since 2006. Monitoring of CO2 emissions from new vans started in 2012. Since then, average specific emissions have decreased by 6.6 %. In 2016, average emissions decreased by a further 4.7 g CO2/km, a 9.2 % decrease from 2012 levels.
Even though emissions from newly registered passenger cars and vans are well below the target path, they will need to further decrease by almost 20 % for new passenger cars and by more than 11 % for vans in order to meet the targets of 95 g CO2/km by 2021 and 147 g CO2/km by 2020 respectively. CO2 emissions from passenger cars and vans officially reported by Member States and vehicle manufacturers. While these emission values are based on measurements performed in the laboratory using the standard European vehicle test cycle, it is nowadays widely accepted that such measurements may not reflect real-world driving performance.
The European Commission has recently proposed setting new CO2 emission standards for cars and vans for the period after 2020. The proposed framework foresees a 30 % reduction of average emissions by 2030 compared with 2021.
Transport remains very dependent on oil, with oil-derived fuels accounting for 95 % of final energy consumption in transport. After reaching a peak in 2007, the impacts of the economic recession caused a subsequent decline in transport demand — oil consumption continuously decreased, until in 2013 it was 12.5 % below 2007 levels. From 2013 to 2015, the trend was upwards, although levels remained 8.8 % below those of 2008.
Road transport is responsible for the largest share of oil-derived fuels in transport, accounting for 78 % of total consumption in the EU-28 in 2015. Despite a decrease in energy consumption since the recession, road transport energy consumption in 2015 was still 23 % higher than in 1990. The portion of diesel used in road transport has continued to increase, amounting to more than 66 % of total fuel sales in road transport in 2015, compared with 51 % in 2000. This trend confirms the increasing dieselisation of Europe’s vehicle fleet over the same period.
In order to achieve the 2050 goal of 70 % a reduction in transport oil consumption compared with 2008, the additional efforts required remain challenging. Even though the EU was on the target path until 2014, the increase in diesel fuel consumption in road transport and international marine bunkers meant it exceeded the projected downward target trend in 2015. Transport oil consumption will need to fall by more than two thirds to meet the objectives of a 70 % reduction in oil consumption by 2050.
Only those biofuels complying with the sustainability criteria under the Renewable Energy Directive and the Fuel Quality Directive are considered for this target. According to preliminary EEA estimates for 2016 (EEA, 2017b), the share of renewable energy grew from 6.7 % in 2015 to 7.1 % in 2016 (Table 1). For the EU-28 overall, the observed trend lies below the target path to reach the 2020 goal. The share of renewable energy in transport varied across countries, from 27 % (Sweden) to close to 0.5 % (Estonia). Besides Sweden, two more Member States (Austria and Finland) have also reached the goal of a 10 % share of energy from renewable sources in transport.
Renewable energy in this sector comes overwhelmingly from biofuels (close to 90 %), with electricity still playing only a limited role. A larger share of renewable electricity use in the transport sector would reduce the pressure on transport biofuels to reach the EU's target of a 10 % renewable energy share (RES) consumed in transport by 2020 (EEA, 2017b).
Between 2000 and 2015, because of the introduction of fuel quality standards, Euro vehicle emission standards and the use of cleaner technologies, the transport sector significantly reduced emissions of certain air pollutants: sulphur oxides (SOx), nitrogen oxides (NOx) and particulate matter (PM) (TERM 003 indicator). With the exception of international aviation, all modes of transport contributed to the decrease.
Transport is responsible for more than half of all NOx emissions and contributes significantly to the total emissions of the other pollutants. Road transport, in particular, continues to make a significant contribution to emissions of all the main air pollutants (with the exception of SOx). Some 39 % of NOx emissions arise from road transport. However, the contribution of the road transport sector to harmful NO2 concentrations, especially in urban areas, is considerably higher, because emissions occur close to the ground and are distributed over densely populated areas.
While emissions from road transport are mostly exhaust emissions arising from fuel combustion, non-exhaust emissions contribute to both non-methane volatile organic compounds (NMVOCs) (from fuel evaporation) and primary particulate matter (PM) (from tyre- and brake-wear, and road abrasion). Although emissions of fine particulate matter (PM2.5) from road transport have declined by 50 % since 2000, the relative importance of non-exhaust emissions has increased, because the introduction of vehicle particulate abatement technologies has reduced exhaust emissions.
As land-based emissions from transport sources decrease, there is an increased focus on coastal maritime emissions which contribute to background air pollution across Europe. Initiatives to reduce emissions of key air pollutants from the maritime sector include an international agreement to limit the maximum sulphur content in maritime fuel to 0.5% from 2020, and already from 2015 establishing a maximum concentration of 0.1% in a sulphur emission control area covering the Baltic Sea, the North Sea and the English Channel. For NOx, a similar emission control area covering the same region is foreseen from 2021.
Noise pollution is a significant environmental health problem in Europe, with road traffic the dominant source of environmental noise. The latest data reported by EEA member countries (TERM 005 indicator) show that around 100 million people are exposed to road traffic noise levels above the 55 dB Lden indicator[1]. Exposure to noise from railways comes next with 19 million people exposed above 55 dB Lden. Aircraft noise, with more than 4.1 million people exposed above 55 dB Lden, is the third main noise source. While aircraft noise does not affect a wide geographical area, aircraft typically generate more annoyance and sleep disturbance than other sources at the same noise levels.
Transport can also cause several significant negative impacts on ecosystems and biodiversity. The design and use of road, rail and waterborne transport infrastructure alters the quality and connectivity of habitats and can create physical barriers to the movement of plants and animals between habitat areas. Species can be injured or killed by vehicles, become isolated by habitat fragmentation, or exhibit behavioural changes that put their survival at risk, such as feeding on or near roads, or changes in migratory behaviour (Bennett et al., 2011; CEEweb, 2011). The development and use of transport infrastructure can also increase pollution levels in surrounding habitats and serve as a vector for the spread of non-native and invasive species (von der Lippe and Kowarik, 2008). A number of policies have been introduced, establishing procedures and obligations to minimise such consequences. However, several gaps remain concerning their implementation in practical terms (EEA, 2015).
TERM 001: Final energy consumption by mode of transport
TERM 002: Greenhouse gas emissions from transport
TERM 003: Emissions of air pollutants from transport
TERM 004: Exceedance of air quality objectives due to traffic
TERM 005: Population exposure to environmental noise
TERM 012: Passenger transport demand
TERM 013: Freight transport demand
TERM 020: Real change in transport prices by mode
TERM 021: Transport fuel prices and taxes
TERM 031: Use of renewable fuels in transport
TERM 032: Size of the vehicle fleet
TERM 034: Alternative-fuel vehicles as a proportion of the total fleet
Bennett, V. J., Smith, W. P. and Betts, M. G., 2011, Toward Understanding the Ecological Impact of Transportation Corridors, General Technical Report, PNW-GTR-846, US Department of Agriculture, Forest Service (https://www.fs.fed.us/pnw/pubs/pnw_gtr846.pdf).
CEEweb, 2011, 'Land Use and Green Infrastructure' (http://www.ceeweb.org/wp-content/uploads/2011/12/landuse_factsheet_GI.pdf).
EEA, 2015, ‘Evaluating 15 years of transport and environmental policy integration — TERM 2015: Transport indicators tracking progress towards environmental targets in Europe’, European Environment Agency (https://www.eea.europa.eu//publications/term-report-2015) accessed 26 October 2017.
EEA, 2017a, ‘Approximated European Union greenhouse gas inventory: Proxy GHG emission estimates for 2016’, European Environment Agency (https://www.eea.europa.eu/themes/climate/approximated-greenhouse-gas-emissions/approximated-greenhouse-gas-emissions-in-2016).
EEA, 2017b, ‘Renewable energy in Europe 2017: recent growth and knock-on effects’, European Environment Agency (https://www.eea.europa.eu/publications/renewable-energy-in-europe-2017).
von der Lippe, M. and Kowarik, I., 2008, 'Do cities export biodiversity? Traffic as dispersal vector across urban–rural gradients', Diversity and Distributions 14(1), 18–25 (http://onlinelibrary.wiley.com/doi/10.1111/j.1472-4642.2007.00401.x/full).
For references, please go to https://www.eea.europa.eu/publications/monitoring-progress-of-europe2019s-transport/monitoring-progress-of-europes-transport or scan the QR code.
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