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Directive 2011/76/EU of the European Parliament and of the Council of 27 September 2011 amending Directive 1999/62/EC on the charging of heavy goods vehicles for the use of certain infrastructures (Text with EEA relevance)
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This is the original version (as it was originally adopted).
This Annex sets out the minimum requirements for levying an external-cost charge and for calculating the maximum weighted average external-cost charge.
The Member State shall specify precisely the part or parts of their road network which are to be subject to an external-cost charge.
Where a Member State chooses to levy an external-cost charge on only a part or parts of the road network falling within the scope of this Directive, the part or parts shall be chosen after an assessment establishing that:
vehicles’ use of the roads where the external-cost charge is applied generates environmental damage higher than that generated on average on other parts of the road network falling within the scope of this Directive that are not subject to an external-cost charge, or
the imposition of an external-cost charge on other parts of the road network falling within the scope of this Directive might have adverse effects on the environment or road safety, or levying and collecting an external-cost charge on them would entail disproportionate cost.
The Member State shall notify the Commission of the classification of vehicles according to which the toll shall vary. It shall also notify the Commission of the location of roads subject to higher external-cost charges (called hereafter “suburban roads (including motorways)”), and of roads subject to lower external-cost charges (called hereafter “interurban roads (including motorways)”).
Where applicable, it shall also notify the Commission of the exact time periods corresponding to the night period during which a higher external noise-cost charge may be imposed to reflect greater noise nuisances.
The classification of roads as suburban roads (including motorways) and interurban roads (including motorways), and the definition of time periods shall be based on objective criteria related to the level of exposure of the roads and their vicinities to pollution such as population density, and the yearly number of pollution peaks measured in accordance with this Directive. The criteria used shall be included in the notification.
For each vehicle class, type of road and time period, the Member State or, if appropriate, an independent authority shall determine a single specific amount. The resulting charging structure, including the start time and the end time of each night period where the external-cost charge includes the cost of noise pollution, shall be transparent, made public and available to all users on equal terms. The publication should occur in a timely manner before implementation. All parameters, data and other information necessary to understand how the various external-cost elements are calculated shall be made public.
When setting the charges, the Member State or, if appropriate, an independent authority shall be guided by the principle of efficient pricing that is a price close to the social marginal cost of the usage of the vehicle charged.
The charge shall also be set after having considered the risk of traffic diversion together with any adverse effects on road safety, the environment and congestion, and any solutions to mitigate these risks.
The Member State or, if appropriate, an independent authority, shall monitor the effectiveness of the charging scheme in reducing environmental damage arising from road transport. It shall every two years adjust, if appropriate, the charging structure and the specific amount of the charge set for a given class of vehicle, type of road and period of time to the changes in transport supply and demand.
When a Member State chooses to include all or part of the cost of traffic-based air pollution in the external-cost charge, the Member State or, if appropriate, an independent authority shall calculate the chargeable cost of traffic–based air pollution by applying the following formula or by taking the unit values in Table 1 of Annex IIIb if the latter are lower:
where:
=
air pollution cost of vehicle class i on road type j (euro/vehicle.kilometre)
=
emission factor of pollutant k and vehicle class i (gram/vehicle.kilometre)
=
monetary cost of pollutant k for type of road j (euro/gram)
The emission factors shall be the same as those used by the Member State to draft the national emissions inventories provided for in Directive 2001/81/EC of the European Parliament and of the Council of 23 October 2001 on national emission ceilings for certain atmospheric pollutants(1) (which requires use of the EMEP/CORINAIR Emission Inventory Guidebook(2)). The monetary cost of pollutants shall be estimated by the Member State or, if appropriate, an independent authority, respecting the state of the article
The Member State or, if appropriate, an independent authority may apply scientifically proven alternative methods to calculate the value of air pollution costs using data from air pollutant measurement and the local value of the monetary cost of air pollutants, provided that the results do not exceed the unit values referred to in Table 1 of Annex IIIb for any class of vehicles.
When a Member State chooses to include all or part of the cost of traffic-based noise pollution in the external-cost charge, the Member State or, if appropriate, an independent authority shall calculate the chargeable cost of traffic–based noise pollution by applying the following formulae or by taking the unit values in Table 2 of Annex IIIb if the latter are lower:
where:
noise cost of one heavy goods vehicle on road type j (euro/vehicle.kilometre)
noise cost per person exposed on road type j to noise level k (euro/person)
population exposed to daily noise level k per kilometre (person/kilometre)
weighted average daily traffic (passenger car equivalent)
are weighting factors determined by the Member State in such a way that the resulting weighted average noise charge per vehicle kilometre does not exceed NCVj (daily).
The traffic-based noise pollution relates to the impact on noise levels measured close to the point of exposure and behind anti-noise barriers, if any.
The population exposed to noise level k shall be taken from the strategic noise maps drafted under Article 7 of Directive 2002/49/EC of the European Parliament and the Council of 25 June 2002 relating to the assessment and management of environmental noise(3).
The cost per person exposed to noise level k shall be estimated by the Member State or, if appropriate, an independent authority, respecting the state of the article
The weighted average daily traffic shall assume an equivalence factor “e” of no more than 4 between heavy goods vehicles and passenger cars.
The Member State or, if appropriate, an independent authority may apply scientifically proven alternative methods to calculate the value of noise costs provided that the results do not exceed the unit values referred to in Table 2 of Annex IIIb.
The Member State or, if appropriate, an independent authority, may establish differentiated noise charges to reward the use of quieter vehicles provided it does not result in discrimination against foreign vehicles. If differentiated noise charges are introduced, the charges for the noisiest category of vehicles may not exceed the unit values referred to in Table 2 of Annex IIIb and four times the noise charge for the quietest vehicle.
This Annex sets out the parameters to be used to calculate the maximum weighted average external-cost charge.
cent/vehicle.kilometre | Suburban roads(including motorways) | Interurban roads(including motorways) |
---|---|---|
EURO 0 | 16 | 12 |
EURO I | 11 | 8 |
EURO II | 9 | 7 |
EURO III | 7 | 6 |
EURO IV | 4 | 3 |
EURO V | 0 | 0 |
after 31 December 2013 | 3 | 2 |
EURO VI | 0 | 0 |
after 31 December 2017 | 2 | 1 |
Less polluting than EURO VI | 0 | 0 |
The values of Table 1 may be multiplied by a factor of up to 2 in mountain areas to the extent that it is justified by the gradient of roads, altitude and/or temperature inversions.
cent/vehicle.kilometre | Day | Night |
---|---|---|
Suburban roads (including motorways) | 1,1 | 2 |
Interurban roads (including motorways) | 0,2 | 0,3 |
The values in Table 2 may be multiplied by a factor of up to 2 in mountain areas to the extent that it is justified by the gradient of roads, temperature inversions and/or amphitheatre effect of valleys.
.’.
Methodology of the European Environmental Agency: http://reports.eea.europa.eu/EMEPCORINAIR5/
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