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Indicator Specification
Transport is one of the main sources of greenhouse gases and also gives rise to significant air pollution, which can seriously damage human health and ecosystems. Reducing demand would consequently reduce freight transport's environmental burden. Decoupling the need for freight transport from GDP growth is only indirectly linked to environmental impact.
The relevance of the modal split policy for environmental impact of freight transport arises from differences in environmental performance (resource consumption, greenhouse gas emissions, pollutant and noise emissions, land consumption, accidents etc.) of transport modes. These differences are becoming smaller on a tonne-km basis, which makes it increasingly difficult to determine the direct and future overall environmental effects of modal shifting. Additionally the differences in performance within specific modes can be substantial as for example old trains versus new trains. The total environmental effect of modal shifting can in fact only be determined on a case-by-case basis, where local circumstances and specific local environmental effects can be taken into account (e.g. transport in urban areas or through sensitive areas). The magnitude of environmental effects from modal shifting may be limited, as modal shift is only an option for small market segments. Opportunities for modal shifting depend amongst others on the type of goods lifted - e.g. perishable goods or bulk goods - and the specific transport requirements for these goods.
The outlook presents plausible future of transport developments in pan-European region and can be used for estimation of fright transport impact on environment (particularly when it comes to transport contribution to climate change). It helps to assess achievability of targets and identify appropriate policy response options for making transportation more sustainable.
Definition: Freight transport activity or freight transport demand is the total volume of freight transport in tonne-km travelled. Modal split covers public trucks, rail transport and inland navigation. It should be noted that inland navigation includes both waterborne inland transport activity and domestic sea shipping. However, international short sea shipping is not included in the above category as, according to EUROSTAT energy balances, energy needs for international shipping are allocated to bunkers.
Model used: PRIMES
Ownership: European Environment Agency
Temporal coverage: 1990 - 2030
Geographical coverage: EU25: Austria, Belgium, Denmark, Finland, France, Germany, Greece, Ireland, Italy, Luxembourg, Netherlands, Portugal, Spain, Sweden, United Kingdom, Cyprus, Czech republic, Estonia, Hungary, Latvia, Lithuania, Malta, Poland, Slovakia, Slovenia
The large number of non binding policy instruments have been developed under fora such as Environment for Europe process, the European Council of Ministers of Transport (ECMT) and the UNECE/WTO Transport, Health and Environment Pan-European Programme (The PEP). The PEP was set up to address the key challenges to achieve more sustainable transport patterns and a closer integration of environmental and health concerns into transport policies.
The EU has set itself the objective to reduce the link between economic growth and freight transport demand ('decoupling') in order to achieve more sustainable transport.
Reducing the link between transport growth and GDP is a central theme in EU transport policy for reducing the negative impacts from transport:
Shifting freight from road to water and rail is an important strategic element in the EU transport policy. The objective was first formulated in the Sustainable Development Strategy ("SDS"). In the review of the T&E integration strategy in 2001 and 2002, the Council states that the modal split should remain stable for at least the next ten years, even with further traffic growth. In the White Paper on the Common Transport Policy (CTP) "European Transport Policy for 2010: Time to Decide", the Commission proposes a number of measures aimed at the modal shift.
The White Paper on the Common Transport Policy also says that common transport policy alone will not provide all the answers. It must be part of an overall strategy integrating sustainable development, to include: a) economic policy and changes in the production process that influence demand for transport; b) land-use planning policy and in particular town planning; c) social and education policy; d) urban transport policy; e) budgetary and fiscal policy to, to link the internalisation of external, and especial environmental, costs with competition of trans-European network; f) competition policy, to ensure, in line with the objectives of high-quality public services, and in particularly in rail sector, that the opening-up of market is not harmed by the dominant companies already present on market; g) research policy for transport in Europe.
Motorways of the sea are alternative routes which could relieve bottlenecks on land. The member States are jointly invited to establish transnational maritime links. (TEN)
The European Neighborhood Policy stressed that generating more trade and tourism between the Union and its neighbours, requires efficient, multimodal and sustainable transport systems. EU should develop an Actions plan for cooperation with its neighbors to improve the physical transport networks connecting the Union with neighboring countries, to step up aviation relations with partner countries with the aim to open up markets and to co-operate on safety and security issues. The Action Plans will also contain specific provisions to address the vulnerability of transport networks and services vis-A-vis terrorist attacks. The highest attention will be paid to enhance the security of air and maritime transport.
EECCA Environmental Strategy recognizes the need to incorporate environmental concerns into transport policies and sets this action as one of the Strategy objectives.
EU Strategy for Sust.Dev. (A Sustainable Europe for a Better World)
WTP: White Paper on the Common Transport Policy (European transport policy for 2010: time to decide)
UNECE/WHO Transport, Health and Environment Pan-European Prigramme
SDS: Environmental Partnerships in the UNECE Region: Environment Strategy for Countries of Eastern Europe, Caucasus and Central Asia Strategic Framework. Fifth MInisterial Conference Environment for Europe. Kiev, Ukraine, 21-23 May 2003
The European Neighborhood Policy
Structural goals and targets
Global
- Implement transport strategies for sustainable development (WSSD)
Pan-European
- ... "develop transport infrastructure further through ... networks, better traffic management ... and intermodal approach" (ECMT, Council of Ministers, 1997)
EU
- Maintain 35% rail modal share for freight in EU10 by 2015 (2001 White Paper)
- Increase railway freight share from 8 to 15% by 2020 (2001 White Paper + rail industry)
- A single European railway system (2001 White Paper + rail industry)
- "...a shift in transport use from road to rail, water and public passenger transport .. [so] the share of road transport in 2010 is no greater than in 1998" (EU Sustainable Development Strategy, 2001)
EECCA
- incentives for sustainable transport (EECCA Strategy)
- modernization of transportation facilities, including use of less energy intensive transport modes (EECCA Strategy)
Efficiency targets
Pan-European
- Promoting demand-side management and modal shift (the PEP )
EU
- Decouple transport growth significantly from GDP (6th EAP)
- "...a switch to more efficient and cleaner forms of transport including better organization and logistics" (6EAP)
EECCA
-...emphasis on demand management" (EECCA Strategy)
Link to other policy goals and targets
Pan-European
- Integration of environment and health into transport policy
-"..reducing greenhouse gas emissions in the transport sector
- "..Better integration of land-use and transport planning."
- "develop transport infrastructure further through networks, better traffic management. "
- Extension of pan-European transport corridors to neighboring areas (2004 Santiago de Compostela Conference)
- TEN established by 2020 (884/2004/CE)
EU
- 140g CO2 average passenger car fleet emissions by 2008
120g CO2 by 2012 (EC/industry agreement)
- Noise from transport is reduced and is no longer presents a health concern
- "introduction of road pricing" (EU Sust. Dev. Strategy, 2001)
- "promoting measures to reflect the full environmental costs in the price of transport" (6EAP)
- Promote more balanced regional development (EU 2001 Sust. Dev. Strategy)
- Link sea, inland water and rail transport
- Improve efficiency of intermodal services (2001 White Paper on Transport)
EECCA
- Develop and implement national transport strategies for sustainable development to: improve affordability, efficiency, convenience, GHG emissions, urban air quality, health (EECCA Strategy)
- Introduce vehicle and fuel standards (EECCA Strategy)
The indicator of the Freight transport activity is produced using the transport module of PRIMES model. The model covers the horizon from 1990 to 2030 with 5 years periods.
PRIMES is a partial equilibrium model for the European Union energy system developed by, and maintained at, The National Technical University of Athens, E3M-Laboratory. The most recent version of the model used in the calculations covers each of the EU Member States, EU candidate countries and Neighbouring countries, uses Eurostat as the main data source, and is updated with 2000 as the base year. The PRIMES model is the result of collaborative research under a series of projects supported by the Joule programme of the Directorate General for Research of the European Commission.
The transport module of PRIMES has been developed to study mainly the penetration of new transport technologies and their effects on emissions, besides the evaluation of the energy consumption and emissions in the transport sector. The emphasis is on the use of car technologies and on the long term (2030). The model structure is kept deliberately simple as it is made to interact as demand module with supply modules (refineries, new fuel production) of PRIMES.
The transport sector distinguishes passenger transport and goods transport as separate sectors. They are further subdivided in sub-sectors according to the transport mode (road, air, etc.). At the level of the sub-sectors, the model structure defines several technology types (car technology types, for example), which correspond to the level of energy use.
The overall demand for transport (passenger kilometres, ton kilometres) is determined by income/activity growth and by the overall price of transport. The overall price of transport is determined endogenously, as a function of the modal split and of the price per mode. The split of the overall transport activity over the different modes is driven by the price per mode and by behavioural and structural parameters. The price per mode depends on the choice of technology for new investment and on past investment for each transport mode. The technologies for new investment are chosen, based on the lowest expected usage costs.
The stock of vehicles inherited from the previous period is expanded in function of the transport needs per mode. The new stock composition determines the stock for the next period and influences the aggregate price per mode.
For more information see: http://www.e3mlab.ntua.gr/DEFAULT.HTM
No methodology for gap filling has been specified. Probably this info has been added together with indicator calculation.
No uncertainty has been specified
No uncertainty has been specified
No uncertainty has been specified
Work specified here requires to be completed within 1 year from now.
Work specified here will require more than 1 year (from now) to be completed.
For references, please go to https://www.eea.europa.eu/data-and-maps/indicators/freight-transport-demand-outlook-from-eea or scan the QR code.
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