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Document 01998L0070-20181224
Directive 98/70/EC of the European Parliament and of the Council of 13 October 1998 relating to the quality of petrol and diesel fuels and amending Council Directive 93/12/EEC
Consolidated text: Directive 98/70/EC of the European Parliament and of the Council of 13 October 1998 relating to the quality of petrol and diesel fuels and amending Council Directive 93/12/EEC
Directive 98/70/EC of the European Parliament and of the Council of 13 October 1998 relating to the quality of petrol and diesel fuels and amending Council Directive 93/12/EEC
01998L0070 — EN — 24.12.2018 — 008.001
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DIRECTIVE 98/70/EC OF THE EUROPEAN PARLIAMENT AND OF THE COUNCIL of 13 October 1998 relating to the quality of petrol and diesel fuels and amending Council Directive 93/12/EEC (OJ L 350 28.12.1998, p. 58) |
Amended by:
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Official Journal |
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No |
page |
date |
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L 287 |
46 |
14.11.2000 |
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DIRECTIVE 2003/17/EC OF THE EUROPEAN PARLIAMENT AND OF THE COUNCIL of 3 March 2003 |
L 76 |
10 |
22.3.2003 |
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REGULATION (EC) No 1882/2003 OF THE EUROPEAN PARLIAMENT AND OF THE COUNCIL of 29 September 2003 |
L 284 |
1 |
31.10.2003 |
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DIRECTIVE 2009/30/EC OF THE EUROPEAN PARLIAMENT AND OF THE COUNCIL of 23 April 2009 |
L 140 |
88 |
5.6.2009 |
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L 147 |
15 |
2.6.2011 |
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L 170 |
62 |
11.6.2014 |
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DIRECTIVE (EU) 2015/1513 OF THE EUROPEAN PARLIAMENT AND OF THE COUNCIL of 9 September 2015 |
L 239 |
1 |
15.9.2015 |
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REGULATION (EU) 2018/1999 OF THE EUROPEAN PARLIAMENT AND OF THE COUNCIL of 11 December 2018 |
L 328 |
1 |
21.12.2018 |
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DIRECTIVE 98/70/EC OF THE EUROPEAN PARLIAMENT AND OF THE COUNCIL
of 13 October 1998
relating to the quality of petrol and diesel fuels and amending Council Directive 93/12/EEC
Article 1
Scope
This Directive sets, in respect of road vehicles, and non-road mobile machinery (including inland waterway vessels when not at sea), agricultural and forestry tractors, and recreational craft when not at sea:
technical specifications on health and environmental grounds for fuels to be used with positive ignition and compression-ignition engines, taking account of the technical requirements of those engines; and
a target for the reduction of life cycle greenhouse gas emissions.
Article 2
Definitions
For the purposes of this Directive:
‘petrol’ means any volatile mineral oil intended for the operation of internal combustion positive-ignition engines for the propulsion of vehicles and falling within CN codes 2710 11 41 , 2710 11 45 , 2710 11 49 , 2710 11 51 and 2710 11 59 ( 1 );
‘diesel fuels’ means gas oils falling within CN code 2710 19 41 (1) and used for self-propelling vehicles as referred to in Directive 70/220/EEC and Directive 88/77/EEC;
‘gas oils intended for use by non-road mobile machinery (including inland waterway vessels), agricultural and forestry tractors, and recreational craft’ means any petroleum-derived liquid, falling within CN codes 2710 19 41 and 2710 19 45 ( 2 ), intended for use in compression ignition engines referred to in Directives 94/25/EC ( 3 ), 97/68/EC ( 4 ) and 2000/25/EC ( 5 );
‘outermost regions’ means France with regard to the French overseas departments, Portugal with regard to the Azores and Madeira, and Spain with regard to the Canary Islands;
‘Member States with low ambient summer temperatures’ means Denmark, Estonia, Finland, Ireland, Latvia, Lithuania, Sweden and the United Kingdom;
‘life cycle greenhouse gas emissions’ means all net emissions of CO2, CH4 and N2O that can be assigned to the fuel (including any blended components) or energy supplied. This includes all relevant stages from extraction or cultivation, including land-use changes, transport and distribution, processing and combustion, irrespective of where those emissions occur;
‘greenhouse gas emissions per unit of energy’ means the total mass of CO2 equivalent greenhouse gas emissions associated with the fuel or energy supplied, divided by the total energy content of the fuel or energy supplied (for fuel, expressed as its low heating value);
‘supplier’ means the entity responsible for passing fuel or energy through an excise duty point or, if no excise is due, any other relevant entity designated by a Member State;
‘biofuels’ has the same meaning as in Directive 2009/28/EC of the European Parliament and of the Council of 23 April 2009 on the promotion of the use of energy from renewable sources ( 6 );
‘renewable liquid and gaseous transport fuels of non-biological origin’ means liquid or gaseous fuels other than biofuels whose energy content comes from renewable energy sources other than biomass, and which are used in transport;
‘starch-rich crops’ means crops comprising mainly cereals (regardless of whether only the grains are used or the whole plant, such as in the case of green maize, is used), tubers and root crops (such as potatoes, Jerusalem artichokes, sweet potatoes, cassava and yams), and corm crops (such as taro and cocoyam);
‘low indirect land-use change-risk biofuels’ means biofuels, the feedstocks of which were produced within schemes which reduce the displacement of production for purposes other than for making biofuels and which were produced in accordance with the sustainability criteria for biofuels set out in Article 7b;
‘processing residue’ means a substance that is not the end product(s) that a production process directly seeks to produce; it is not a primary aim of the production process and the process has not been deliberately modified to produce it;
‘agricultural, aquaculture, fisheries and forestry residues’ means residues that are directly generated by agriculture, aquaculture, fisheries and forestry; they do not include residues from related industries or processing.
▼M4 —————
Article 3
Petrol
However, Member States may, for the outermost regions, make specific provisions for the introduction of petrol with a maximum sulphur content of 10 mg/kg. Member States making use of this provision shall inform the Commission accordingly.
Member States in which the derogation referred to in the first subparagraph is not applied may, subject to paragraph 5, permit the placing on the market during the summer period of petrol containing ethanol with a maximum vapour pressure of 60 kPa and in addition the permitted vapour pressure waiver specified in Annex III, on condition that the ethanol used is a biofuel.
Where Member States wish to apply either of the derogations provided for in paragraph 4, they shall notify the Commission and provide all relevant information. The Commission shall assess the desirability and duration of the derogation, taking account of both:
the avoidance of socioeconomic problems resulting from higher vapour pressure, including time-limited technical adaptation needs; and
the environmental or health consequences of the higher vapour pressure and, in particular, the impact on compliance with Community legislation on air quality, both in the Member State concerned and in other Member States.
If the Commission's assessment shows that the derogation will result in a lack of compliance with Community legislation on air quality or air pollution, including the relevant limit values and emissions ceilings, the application shall be rejected. The Commission should also take account of relevant target values.
Where the Commission has raised no objections within six months of receipt of all relevant information, the Member State concerned may apply the requested derogation.
▼M4 —————
Article 4
Diesel fuel
Notwithstanding the requirements of Annex II, Member States may permit the placing on the market of diesel with a fatty acid methyl ester (FAME) content greater than 7 %.
Member States shall ensure the provision of appropriate information to consumers concerning the biofuel, in particular FAME, content of diesel fuel.
However, in order to accommodate minor contamination in the supply chain, Member States may, from 1 January 2011, permit gas oil intended for use by non-road mobile machinery (including inland waterway vessels), agricultural and forestry tractors and recreational craft to contain up to 20 mg/kg of sulphur at the point of final distribution to end users. Member States may also permit the continued placing on the market until 31 December 2011 of gas oil containing up to 1 000 mg/kg sulphur for rail vehicles and agricultural and forestry tractors, provided that they can ensure that the proper functioning of emissions control systems will not be compromised.
Article 5
Free circulation
No Member State may prohibit, restrict or prevent the placing on the market of fuels which comply with the requirements of this Directive.
Article 6
Marketing of fuels with more stringent environmental specifications
▼M2 —————
Article 7
Change in supply of crude oils
If, as a result of exceptional events, a sudden change in the supply of crude oils or petroleum products renders it difficult for the refineries in a Member State to respect the fuel specification requirements of Articles 3 and 4, that Member State shall inform the Commission thereof. The Commission, after informing the other Member States, may authorise higher limit values in that Member State for one or more fuel components for a period not exceeding six months.
The Commission shall notify the Member States and inform the European Parliament and the Council of its decision.
Any Member State may refer the Commission's decision to the Council within one month of its notification.
The Council, acting by a qualified majority, may take a different decision within one month of the matter being referred to it.
Article 7a
Greenhouse gas emission reductions
In the case of suppliers of biofuels for use in aviation, Member States may permit such suppliers to choose to become contributors to the reduction obligation laid down in paragraph 2 of this Article provided that that those biofuels comply with the sustainability criteria set out in Article 7b.
With effect from 1 January 2011, suppliers shall report annually, to the authority designated by the Member State, on the greenhouse gas intensity of fuel and energy supplied within each Member State by providing, as a minimum, the following information:
the total volume of each type of fuel or energy supplied; and
life cycle greenhouse gas emissions per unit of energy.
Member States shall ensure that reports are subject to verification.
The Commission shall, where appropriate, establish guidelines for the implementation of this paragraph.
Member States shall require suppliers to reduce as gradually as possible life cycle greenhouse gas emissions per unit of energy from fuel and energy supplied by up to 10 % by 31 December 2020, compared with the fuel baseline standard set out in Annex II to Council Directive (EU) 2015/652. That reduction shall consist of:
6 % by 31 December 2020. Member States may require suppliers, for this reduction, to comply with the following intermediate targets: 2 % by 31 December 2014 and 4 % by 31 December 2017;
an indicative additional target of 2 % by 31 December 2020, subject to Article 9(1)(h), to be achieved through one or both of the following methods:
the supply of energy for transport supplied for use in any type of road vehicle, non-road mobile machinery (including inland waterway vessels), agricultural or forestry tractor or recreational craft;
the use of any technology (including carbon capture and storage) capable of reducing life cycle greenhouse gas emissions per unit of energy from fuel or energy supplied;
an indicative additional target of 2 % by 31 December 2020, subject to Article 9(1)(i), to be achieved through the use of credits purchased through the Clean Development Mechanism of the Kyoto Protocol, under the conditions set out in Directive 2003/87/EC of the European Parliament and of the Council of 13 October 2003 establishing a scheme for greenhouse gas emission allowance trading within the Community ( 7 ), for reductions in the fuel supply sector.
Member States may provide that the maximum contribution of biofuels produced from cereal and other starch-rich crops, sugars and oil crops and from crops grown as main crops primarily for energy purposes on agricultural land for the purpose of compliance with the target referred to in the first subparagraph of this paragraph shall not exceed the maximum contribution established in point (d) of the second subparagraph of Article 3(4) of Directive 2009/28/EC.
The Commission shall be empowered to adopt no later than 31 December 2017 delegated acts in order to establish greenhouse gas emission default values, where such values have not already been established prior to 5 October 2015, as regards:
renewable liquid and gaseous transport fuels of non-biological origin;
carbon capture and utilisation for transport purposes.
Article 7b
Sustainability criteria for biofuels
However, biofuels produced from waste and residues, other than agricultural, aquaculture, fisheries and forestry residues, need only fulfil the sustainability criteria set out in paragraph 2 of this Article in order to be taken into account for the purposes referred to in Article 7a.
In the case of installations that were in operation on or before 5 October 2015, for the purposes referred to in paragraph 1, biofuels shall achieve a greenhouse gas emission saving of at least 35 % until 31 December 2017 and at least 50 % from 1 January 2018.
The greenhouse gas emission saving from the use of biofuels shall be calculated in accordance with Article 7d(1).
Biofuels taken into account for the purposes referred to in paragraph 1 shall not be made from raw material obtained from land with high biodiversity value, namely, land that had one of the following statuses in or after January 2008, whether or not the land continues to have such a status:
primary forest and other wooded land, that is forest and other wooded land of native species, where there is no clearly visible indication of human activity and the ecological processes are not significantly disturbed;
areas designated:
by law or by the relevant competent authority for nature protection purposes; or
for the protection of rare, threatened or endangered ecosystems or species recognised by international agreements or included in lists drawn up by intergovernmental organisations or the International Union for the Conservation of Nature, subject to their recognition in accordance with the second subparagraph of Article 7c(4);
unless evidence is provided that the production of that raw material did not interfere with those nature protection purposes;
highly biodiverse grassland that is:
natural, namely, grassland that would remain grassland in the absence of human intervention and which maintains the natural species composition and ecological characteristics and processes; or
non-natural, namely, grassland that would cease to be grassland in the absence of human intervention and which is species-rich and not degraded, unless evidence is provided that the harvesting of the raw material is necessary to preserve its grassland status.
▼M7 —————
Biofuels taken into account for the purposes referred to in paragraph 1 shall not be made from raw material obtained from land with high carbon stock, namely, land that had one of the following statuses in January 2008 and no longer has that status:
wetlands, namely, land that is covered with or saturated by water permanently or for a significant part of the year;
continuously forested areas, namely, land spanning more than one hectare with trees higher than five metres and a canopy cover of more than 30 %, or trees able to reach those thresholds in situ;
land spanning more than one hectare with trees higher than five metres and a canopy cover of between 10 % and 30 %, or trees able to reach those thresholds in situ, unless evidence is provided that the carbon stock of the area before and after conversion is such that, when the methodology laid down in Part C of Annex IV is applied, the conditions laid down in paragraph 2 of this Article would be fulfilled.
The provisions of this paragraph shall not apply if, at the time the raw material was obtained, the land had the same status as it had in January 2008.
The Commission shall, every two years, report to the European Parliament and the Council on the impact on social sustainability in the Community and in third countries of increased demand for biofuel, on the impact of Community biofuel policy on the availability of foodstuffs at affordable prices, in particular for people living in developing countries, and on wider development issues. Reports shall address the respect of land use rights. They shall state, both for third countries and Member States that are a significant source of raw material for biofuel consumed within the Community, whether the country has ratified and implemented each of the following Conventions of the International Labour Organisation:
Those reports shall state, both for third countries and Member States that are a significant source of raw material for biofuel consumed within the Community, whether the country has ratified and implemented:
The first report shall be submitted in 2012. The Commission shall, if appropriate, propose corrective action, in particular if evidence shows that biofuel production has a significant impact on food prices.
Article 7c
Verification of compliance with the sustainability criteria for biofuels
Where biofuels are to be taken into account for the purposes of Article 7a, Member States shall require economic operators to show that the sustainability criteria set out in Article 7b(2) to (5) have been fulfilled. For that purpose they shall require economic operators to use a mass balance system which:
allows consignments of raw material or biofuel with differing sustainability characteristics to be mixed;
requires information about the sustainability characteristics and sizes of the consignments referred to in point (a) to remain assigned to the mixture; and
provides for the sum of all consignments withdrawn from the mixture to be described as having the same sustainability characteristics, in the same quantities, as the sum of all consignments added to the mixture.
The information referred to in the first subparagraph shall include in particular information on compliance with the sustainability criteria set out in Article 7b(2) to (5), appropriate and relevant information on measures taken for soil, water and air protection, the restoration of degraded land, the avoidance of excessive water consumption in areas where water is scarce, and appropriate and relevant information concerning measures taken in order to take into account the issues referred to in the second subparagraph of Article 7b(7).
The Commission shall adopt implementing acts in accordance with the examination procedure referred to in Article 11(3), to establish the list of appropriate and relevant information referred to in the first two subparagraphs of this paragraph. The Commission shall ensure, in particular, that the provision of that information does not represent an excessive administrative burden for operators in general or for smallholder farmers, producer organisations and cooperatives in particular.
The obligations laid down in this paragraph shall apply whether the biofuels are produced within the Community or imported.
Member States shall submit to the Commission in aggregated form, the information referred to in the first subparagraph. The Commission shall publish that information on the transparency platform referred to in Article 24 of Directive 2009/28/EC in summary form preserving the confidentiality of commercially sensitive information.
The Commission may decide that voluntary national or international schemes setting standards for the production of biomass products contain accurate data for the purposes of Article 7b(2) or demonstrate that consignments of biofuel comply with the sustainability criteria set out in Article 7b(3) to (5). The Commission may decide that those schemes contain accurate data for the purposes of information on measures taken for the conservation of areas that provide, in critical situations, basic ecosystem services (such as watershed protection and erosion control), for soil, water and air protection, the restoration of degraded land, the avoidance of excessive water consumption in areas where water is scarce and on the issues referred to in the second subparagraph of Article 7b(7). The Commission may also recognise areas for the protection of rare, threatened or endangered ecosystems or species recognised by international agreements or included in lists drawn up by intergovernmental organisations or the International Union for the Conservation of Nature for the purposes of Article 7b(3)(b)(ii).
The Commission may decide that voluntary national or international schemes to measure greenhouse gas savings contain accurate data for the purposes of Article 7b(2).
The Commission may decide that land that falls within the scope of a national or regional recovery programme aimed at improving severely degraded or heavily contaminated land fulfils the criteria referred to in point 9 of Part C of Annex IV.
The voluntary schemes referred to in paragraph 4 (‘the voluntary schemes’) shall regularly, and at least once per year, publish a list of their certification bodies used for independent auditing, indicating for each certification body by which entity or national public authority it was recognised and which entity or national public authority is monitoring it.
In order in particular to prevent fraud, the Commission may, on the basis of a risk analysis or the reports referred to in the second subparagraph of paragraph 6 of this Article, specify the standards of independent auditing and require all voluntary schemes to apply those standards. This shall be done by means of implementing acts adopted in accordance with the examination procedure referred to in Article 11(3). Such acts shall set a time frame by which voluntary schemes need to implement the standards. The Commission may repeal decisions recognising voluntary schemes in the event that those schemes fail to implement such standards in the time frame provided for.
The Commission shall require that each voluntary scheme, on which a decision has been adopted under paragraph 4, submit by 6 October 2016 and annually thereafter by 30 April, a report to the Commission covering each of the points set out in the third subparagraph of this paragraph. Generally, the report shall cover the preceding calendar year. The first report shall cover at least six months from 9 September 2015. The requirement to submit a report shall apply only to voluntary schemes that have operated for at least 12 months.
By 6 April 2017, the Commission shall submit a report to the European Parliament and to the Council analysing the reports referred to in the second subparagraph of this paragraph, reviewing the operation of the agreements referred to in paragraph 4 or voluntary schemes in respect of which a decision has been adopted in accordance with this Article, and identifying best practices. The report shall be based on the best information available, including following consultations with stakeholders, and on practical experience in the application of the agreements or schemes concerned. The report shall analyse the following:
the independence, modality and frequency of audits, both in relation to what is stated on those aspects in the scheme documentation, at the time the scheme concerned was approved by the Commission, and in relation to industry best practice;
the availability of, and experience and transparency in the application of, methods for identifying and dealing with non-compliance, with particular regard to dealing with situations or allegations of serious wrongdoing on the part of members of the scheme;
transparency, particularly in relation to the accessibility of the scheme, the availability of translations in the applicable languages of the countries and regions from which raw materials originate, the accessibility of a list of certified operators and relevant certificates, and the accessibility of auditor reports;
stakeholder involvement, particularly as regards the consultation of indigenous and local communities prior to decision making during the drafting and reviewing of the scheme as well as during audits and the response given to their contributions;
the overall robustness of the scheme, particularly in light of rules on the accreditation, qualification and independence of auditors and relevant scheme bodies;
market updates of the scheme, the amount of feedstocks and biofuels certified, by country of origin and type, the number of participants;
the ease and effectiveness of implementing a system that tracks the proofs of conformity with the sustainability criteria that the scheme gives to its member(s), such a system intended to serve as a means of preventing fraudulent activity with a view, in particular, to the detection, treatment and follow-up of suspected fraud and other irregularities and where appropriate, the number of cases of fraud or irregularities detected;
options for entities to be authorised to recognise and monitor certification bodies;
criteria for the recognition or accreditation of certification bodies;
rules on how the monitoring of the certification bodies is to be conducted;
ways to facilitate or improve the promotion of best practice.
A Member State may notify its national scheme to the Commission. The Commission shall give priority to the assessment of such a scheme. A decision on the compliance of such a notified national scheme with the conditions set out in this Directive shall be adopted in accordance with the examination procedure referred to in Article 11(3), in order to facilitate mutual bilateral and multilateral recognition of schemes for verification of compliance with the sustainability criteria for biofuels. Where the decision is positive, schemes established in accordance with this Article shall not refuse mutual recognition with that Member State's scheme as regards the verification of compliance with the sustainability criteria set out in Article 7b(2) to (5).
By 31 December 2012, the Commission shall report to the European Parliament and to the Council on:
the effectiveness of the system in place for the provision of information on sustainability criteria; and
whether it is feasible and appropriate to introduce mandatory requirements in relation to air, soil or water protection, taking into account the latest scientific evidence and the Community's international obligations.
The Commission shall, if appropriate, propose corrective action.
Article 7d
Calculation of life cycle greenhouse gas emissions from biofuels
For the purposes of Article 7a and Article 7b(2), life cycle greenhouse gas emissions from biofuels shall be calculated as follows:
where a default value for greenhouse gas emission savings for the biofuel production pathway is laid down in Part A or B of Annex IV and where the el value for those biofuels calculated in accordance with point 7 of Part C of Annex IV is equal to or less than zero, by using that default value;
by using an actual value calculated in accordance with the methodology laid down in Part C of Annex IV; or
by using a value calculated as the sum of the factors of the formula referred to in point 1 of Part C of Annex IV, where disaggregated default values in Part D or E of Annex IV may be used for some factors, and actual values, calculated in accordance with the methodology laid down in Part C of Annex IV, for all other factors.
In the event that the reports referred to in the first subparagraph indicate that the estimated typical and default values in Parts B and E of Annex IV might need to be adjusted on the basis of the latest scientific evidence, the Commission shall, as appropriate, submit a legislative proposal to the European Parliament and to the Council.
▼M7 —————
The Commission shall keep Annex IV under review, with a view, where justified, to the addition of values for further biofuel production pathways for the same or for other raw materials. That review shall also consider the modification of the methodology laid down in Part C of Annex IV, particularly with regard to:
The default values for waste vegetable or animal oil biodiesel shall be reviewed as soon as possible. In the event that the Commission's review concludes that additions to Annex IV should be made, the Commission shall be empowered to adopt delegated acts pursuant to Article 10a to add, but not to remove or amend, estimated typical and default values in Parts A, B, D and E of Annex IV for biofuel pathways for which specific values are not yet included in that Annex.
Any adaptation of or addition to the list of default values in Annex IV shall comply with the following:
where the contribution of a factor to overall emissions is small, or where there is limited variation, or where the cost or difficulty of establishing actual values is high, default values must be typical of normal production processes;
in all other cases default values must be conservative compared to normal production processes.
Article 7e
Implementing measures and reports concerning the sustainability of biofuels
Article 8
Monitoring compliance and reporting
Article 8a
Metallic additives
Article 9
Reporting
The Commission shall submit by 31 December 2012, and every three years thereafter, a report to the European Parliament and the Council accompanied, where appropriate, by a proposal for amendments to this Directive. That report shall in particular take account of the following:
the use and evolution of automotive technology and, in particular, the feasibility of increasing the maximum permitted biofuel content of petrol and diesel and the need to review the date referred to in Article 3(3);
Community policy on CO2 emissions from road transport vehicles;
the possibility of applying the requirements of Annex II, and in particular the limit value for polycyclic aromatic hydrocarbons, to non-road mobile machinery (including inland waterways vessels), agricultural and forestry tractors and recreational craft;
the increase in the use of detergents in fuels;
the use of metallic additives other than MMT in fuels;
the total volume of components used in petrol and diesel having regard to Community environmental legislation, including the objectives of Directive 2000/60/EC of the European Parliament and of the Council of 23 October 2000 establishing a framework for Community action in the field of water policy ( 10 ) and its daughter directives;
the consequences of the greenhouse gas reduction target set in Article 7a(2) for the emissions trading scheme;
the potential need for adjustments to Articles 2(6), 2(7) and 7a(2)(b) in order to assess possible contributions for reaching a greenhouse gas reduction target of up to 10 % by 2020. These considerations shall be based on the potential for life cycle greenhouse gas emission reductions from fuels and energy within the Community, taking into account in particular any developments in environmentally safe carbon capture and storage technologies and in electric road vehicles, and the cost effectiveness of means of reducing those emissions, as referred to in Article 7a(2)(b);
the possibility of introducing additional measures for suppliers to reduce by 2 % life cycle greenhouse gas emissions per unit of energy, in comparison with the fuel baseline standard referred to in Article 7a(5)(b), through the use of credits purchased through the Clean Development Mechanism of the Kyoto Protocol under the conditions set out in Directive 2003/87/EC, in order to assess further possible contributions for reaching a greenhouse gas reduction target of up to 10 % by 2020, as referred to in Article 7a(2)(c) of this Directive;
an updated cost-benefit and impact analysis of a reduction in the maximum permitted vapour pressure for petrol for the summer period below 60 kPa;
the production pathways, volumes and the life cycle greenhouse gas emissions per unit of energy, including the provisional mean values of the estimated indirect land-use change emissions and the associated range derived from the sensitivity analysis as set out in Annex V, of the biofuels consumed in the Union. The Commission shall make data on the provisional mean values of the estimated indirect land-use change emissions and the associated range derived from the sensitivity analysis publicly available.
The Commission shall, if appropriate, accompany its report by a proposal for modification of the target.
Article 9a
Penalties
Member States shall determine the penalties applicable to breaches of the national provisions adopted pursuant to this Directive. The penalties determined must be effective, proportionate and dissuasive.
Article 10
Procedure for adaptation of permitted analytical methods and permitted vapour pressure waivers
Article 10a
Exercise of the delegation
Article 11
Committee procedure
Where the Committees deliver no opinion, the Commission shall not adopt the draft implementing act and the third subparagraph of Article 5(4) of Regulation (EU) No 182/2011 shall apply.
Article 12
Repeal and amendment of the Directives related to the fuel quality of petrol and diesel fuels
Article 13
Transposition into national legislation
Member States shall apply these measures from 1 January 2000.
When Member States adopt these measures, they shall contain a reference to this Directive or shall be accompanied by such reference on the occasion of their official publication. The methods of making such reference shall be laid down by Member States.
▼M4 —————
Article 15
Entry into force of the Directive
This Directive shall enter into force on the day of its publication in the Official Journal of the European Communities.
Article 16
Addressees
This Directive is addressed to the Member States.
ANNEX I
ENVIRONMENTAL SPECIFICATIONS FOR MARKET FUELS TO BE USED FOR VEHICLES EQUIPPED WITH POSITIVE-IGNITION ENGINES
Type: Petrol
|
Parameter (1) |
Unit |
Limits (2) |
|
|
Minimum |
Maximum |
||
|
Research octane number |
|
95 (3) |
— |
|
Motor octane number |
|
85 |
— |
|
Vapour pressure, summer period (4) |
kPa |
— |
60,0 (5) |
|
Distillation: |
|
|
|
|
— percentage evaporated at 100 °C |
% v/v |
46,0 |
— |
|
— percentage evaporated at 150 °C |
% v/v |
75,0 |
— |
|
Hydrocarbon analysis: |
|
|
|
|
— olefins |
% v/v |
— |
18,0 |
|
— aromatics |
% v/v |
— |
35,0 |
|
— benzene |
% v/v |
— |
1,0 |
|
Oxygen content |
% m/m |
|
3,7 |
|
Oxygenates |
|
|
|
|
— Methanol |
% v/v |
|
3,0 |
|
— Ethanol (stabilising agents may be necessary) |
% v/v |
|
10,0 |
|
— Iso-propyl alcohol |
% v/v |
— |
12,0 |
|
— Tert-butyl alcohol |
% v/v |
— |
15,0 |
|
— Iso-butyl alcohol |
% v/v |
— |
15,0 |
|
— Ethers containing five or more carbon atoms per molecule |
% v/v |
— |
22,0 |
|
— Other oxygenates (6) |
% v/v |
— |
15,0 |
|
Sulphur content |
mg/kg |
— |
10,0 |
|
Lead content |
g/l |
— |
0,005 |
|
(1)
►M6
Test methods shall be those specified in EN 228:2012. Member States may adopt the analytical method specified in replacement EN 228:2012 standard if it can be shown to give at least the same accuracy and at least the same level of precision as the analytical method it replaces. ◄
(2)
The values quoted in the specification are ‘true values’. In the establishment of their limit values, the terms of EN ISO 4259:2006 ‘Petroleum products — Determination and application of precision data in relation to methods of test’ have been applied and in fixing a minimum value, a minimum difference of 2R above zero has been taken into account (R = reproducibility). The results of individual measurements shall be interpreted on the basis of the criteria described in EN ISO 4259:2006.
(3)
Member States may decide to continue to permit the placing on the market of unleaded regular grade petrol with a minimum motor octane number (MON) of 81 and a minimum research octane number (RON) of 91.
(4)
The summer period shall begin no later than 1 May and shall not end before 30 September. For Member States with low ambient summer temperatures the summer period shall begin no later than 1 June and shall not end before 31 August.
(5)
In the case of Member States with low ambient summer temperatures and for which a derogation is in effect in accordance with Article 3(4) and (5), the maximum vapour pressure shall be 70 kPa. In the case of Member States for which a derogation is in effect in accordance with Article 3(4) and (5) for petrol containing ethanol, the maximum vapour pressure shall be 60 kPa plus the vapour pressure waiver specified in Annex III. |
|||
ANNEX II
ENVIRONMENTAL SPECIFICATIONS FOR MARKET FUELS TO BE USED FOR VEHICLES EQUIPPED WITH COMPRESSION IGNITION ENGINES
Type: Diesel
|
Parameter (1) |
Unit |
Limits (2) |
|
|
Minimum |
Maximum |
||
|
Cetane number |
|
51,0 |
— |
|
Density at 15 °C |
kg/m (3) |
— |
845,0 |
|
Distillation: |
|
|
|
|
— 95 % v/v recovered at: |
°C |
— |
360,0 |
|
Polycyclic aromatic hydrocarbons |
% m/m |
— |
8,0 |
|
Sulphur content |
mg/kg |
— |
10,0 |
|
FAME content — EN 14078 |
% v/v |
— |
7,0 (3) |
|
(1)
►M6
Test methods shall be those specified in EN 590:2013. Member States may adopt the analytical method specified in replacement EN 590:2013 standard if it can be shown to give at least the same accuracy and at least the same level of precision as the analytical method it replaces. ◄
(2)
The values quoted in the specification are ‘true values’. In the establishment of their limit values, the terms of EN ISO 4259:2006 ‘Petroleum products — Determination and application of precision data in relation to methods of test’ have been applied and in fixing a minimum value, a minimum difference of 2R above zero has been taken into account (R = reproducibility). The results of individual measurements shall be interpreted on the basis of the criteria described in EN ISO 4259:2006.
(3)
FAME shall comply with EN 14214. |
|||
ANNEX III
VAPOUR PRESSURE WAIVER PERMITTED FOR PETROL CONTAINING BIOETHANOL
|
Bioethanol content (%v/v) |
Vapour pressure waiver permitted (kPa) (1) |
|
0 |
0 |
|
1 |
3,7 |
|
2 |
6,0 |
|
3 |
7,2 |
|
4 |
7,8 |
|
5 |
8,0 |
|
6 |
8,0 |
|
7 |
7,9 |
|
8 |
7,9 |
|
9 |
7,8 |
|
10 |
7,8 |
|
(1)
The values quoted in the specification are ‘true values’. In the establishment of their limit values, the terms of EN ISO 4259:2006 ‘Petroleum products — Determination and application of precision data in relation to methods of test’ have been applied and in fixing a minimum value, a minimum difference of 2R above zero has been taken into account (R = reproducibility). The results of individual measurements shall be interpreted on the basis of the criteria described in EN ISO 4259:2006. |
|
The permitted vapour pressure waiver for intermediate bioethanol content between the values listed shall be determined by a straight line interpolation between the bioethanol content immediately above and that immediately below the intermediate value.
ANNEX IV
RULES FOR CALCULATING LIFE CYCLE GREENHOUSE EMISSIONS FROM BIOFUELS
A. Typical and default values for biofuels if produced with no net carbon emissions from land use change
|
Biofuel production pathway |
Typical greenhouse gas emission saving |
Default greenhouse gas emission saving |
|
Sugar beet ethanol |
61 % |
52 % |
|
Wheat ethanol (process fuel not specified) |
32 % |
16 % |
|
Wheat ethanol (lignite as process fuel in CHP plant) |
32 % |
16 % |
|
Wheat ethanol (natural gas as process fuel in conventional boiler) |
45 % |
34 % |
|
Wheat ethanol (natural gas as process fuel in CHP plant) |
53 % |
47 % |
|
Wheat ethanol (straw as process fuel in CHP plant) |
69 % |
69 % |
|
Corn (maize) ethanol, Community produced (natural gas as process fuel in CHP plant) |
56 % |
49 % |
|
Sugar cane ethanol |
71 % |
71 % |
|
The part from renewable sources of ethyl-Tertio-butyl-ether (ETBE) |
Equal to that of the ethanol production Pathway used |
|
|
The part from renewable sources of tertiary-amyl-ethyl-ether (TAEE) |
Equal to that of the ethanol production pathway used |
|
|
Rape seed biodiesel |
45 % |
38 % |
|
Sunflower biodiesel |
58 % |
51 % |
|
Soybean biodiesel |
40 % |
31 % |
|
Palm oil biodiesel (process not specified) |
36 % |
19 % |
|
Palm oil biodiesel (process with methane capture at oil mill) |
62 % |
56 % |
|
Waste vegetable or animal (*1) oil biodiesel |
88 % |
83 % |
|
Hydrotreated vegetable oil from rape seed |
51 % |
47 % |
|
Hydrotreated vegetable oil from sunflower |
65 % |
62 % |
|
Hydrotreated vegetable oil from palm oil (process not specified) |
40 % |
26 % |
|
Hydrotreated vegetable oil from palm oil (process with methane capture at oil mill) |
68 % |
65 % |
|
Pure vegetable oil from rape seed |
58 % |
57 % |
|
Biogas from municipal organic waste as compressed natural gas |
80 % |
73 % |
|
Biogas from wet manure as compressed natural gas |
84 % |
81 % |
|
Biogas from dry manure as compressed natural gas |
86 % |
82 % |
|
(*1)
Not including animal oil produced from animal by-products classified as category 3 material in accordance with Regulation (EC) No 1774/2002 of the European Parliament and of the Council of 3 October 2002 laying down health rules concerning animal by-products not intended for human consumption (1)
(1)
OJ L 273, 10.10.2002, p. 1. |
||
B. Estimated typical and default values for future biofuels that were not on the market or were on the market only in negligible quantities in January 2008, if produced with no net carbon emissions from land use change
|
Biofuel production pathway |
Typical greenhouse gas emission saving |
Default greenhouse gas emission saving |
|
Wheat straw ethanol |
87 % |
85 % |
|
Waste wood ethanol |
80 % |
74 % |
|
Farmed wood ethanol |
76 % |
70 % |
|
Waste wood Fischer-Tropsch diesel |
95 % |
95 % |
|
Farmed wood Fischer-Tropsch diesel |
93 % |
93 % |
|
Waste wood dimethylether (DME) |
95 % |
95 % |
|
Farmed wood DME |
92 % |
92 % |
|
Waste wood methanol |
94 % |
94 % |
|
Farmed wood methanol |
91 % |
91 % |
|
The part from renewable sources of methyl-tertio-butyl-ether (MTBE) |
Equal to that of the methanol production pathway used |
|
C. Methodology
|
1. |
Greenhouse gas emissions from the production and use of biofuels shall be calculated as: E = eec + el + ep + etd + eu – esca – eccs – eccr – eee where
Emissions from the manufacture of machinery and equipment shall not be taken into account. |
|
2. |
Greenhouse gas emissions from fuels, E, shall be expressed in terms of grams of CO2 equivalent per MJ of fuel, gCO2eq/MJ. |
|
3. |
By derogation from point 2, values calculated in terms of gCO2eq/MJ may be adjusted to take into account differences between fuels in useful work done, expressed in terms of km/MJ. Such adjustments shall only be made where evidence of the differences in useful work done is provided. |
|
4. |
Greenhouse gas emission savings from biofuels shall be calculated as: SAVING = (EF – EB )/EF where
|
|
5. |
The greenhouse gases taken into account for the purposes of point 1 shall be CO2, N2O and CH4. For the purpose of calculating CO2 equivalence, those gases shall be valued as follows:
|
|
6. |
Emissions from the extraction or cultivation of raw materials, eec, shall include emissions from the extraction or cultivation process itself; from the collection of raw materials; from waste and leakages; and from the production of chemicals or products used in extraction or cultivation. Capture of CO2 in the cultivation of raw materials shall be excluded. Certified reductions of greenhouse gas emissions from flaring at oil production sites anywhere in the world shall be deducted. Estimates of emissions from cultivation may be derived from the use of averages calculated for smaller geographical areas than those used in the calculation of the default values, as an alternative to using actual values. |
|
7. |
Annualised emissions from carbon stock changes caused by land-use change, el, shall be calculated by dividing total emissions equally over 20 years. For the calculation of those emissions, the following rule shall be applied: el = (CSR – CSA) × 3,664 × 1/20 × 1/P – eB, ( 12 ) where
|
|
8. |
The bonus of 29 gCO2eq/MJ shall be attributed if evidence is provided that the land:
(a)
was not in use for agriculture or any other activity in January 2008; and
(b)
falls into one of the following categories:
(i)
severely degraded land, including such land that was formerly in agricultural use;
(ii)
heavily contaminated land. The bonus of 29 gCO2eq/MJ shall apply for a period of up to 10 years from the date of conversion of the land to agricultural use, provided that a steady increase in carbon stocks as well as a sizable reduction in erosion phenomena for land falling under (i) are ensured and that soil contamination for land falling under (ii) is reduced. |
|
9. |
The categories mentioned in point 8(b) are defined as follows:
(a)
‘severely degraded land’ means land that, for a significant period of time, has either been significantly salinated or presented significantly low organic matter content and been severely eroded;
(b)
‘heavily contaminated land’ means land that is unfit for the cultivation of food and feed due to soil contamination. Such land shall include land that has been the subject of a Commission decision in accordance with the fourth subparagraph of Article 7c(3). |
|
10. |
The guide adopted pursuant to point 10 of Part C of Annex V to Directive 2009/28/EC shall serve as the basis of the calculation of land carbon stocks for the purposes of this Directive. |
|
11. |
Emissions from processing, ep , shall include emissions from the processing itself; from waste and leakages; and from the production of chemicals or products used in processing. In accounting for the consumption of electricity not produced within the fuel production plant, the greenhouse gas emission intensity of the production and distribution of that electricity shall be assumed to be equal to the average emission intensity of the production and distribution of electricity in a defined region. As an exception to this rule producers may use an average value for an individual electricity production plant for electricity produced by that plant, if that plant is not connected to the electricity grid. |
|
12. |
Emissions from transport and distribution, etd , shall include emissions from the transport and storage of raw and semi-finished materials and from the storage and distribution of finished materials. Emissions from transport and distribution to be taken into account under point 6 shall not be covered by this point. |
|
13. |
Emissions from the fuel in use, eu , shall be taken to be zero for biofuels. |
|
14. |
Emission savings from carbon capture and geological storage eccs , that have not already been accounted for in ep , shall be limited to emissions avoided through the capture and sequestration of emitted CO2 directly related to the extraction, transport, processing and distribution of fuel. |
|
15. |
Emission savings from carbon capture and replacement, eccr , shall be limited to emissions avoided through the capture of CO2 of which the carbon originates from biomass and which is used to replace fossil-derived CO2 used in commercial products and services. |
|
16. |
Emission savings from excess electricity from cogeneration, eee , shall be taken into account in relation to the excess electricity produced by fuel production systems that use cogeneration except where the fuel used for the cogeneration is a co-product other than an agricultural crop residue. In accounting for that excess electricity, the size of the cogeneration unit shall be assumed to be the minimum necessary for the cogeneration unit to supply the heat that is needed to produce the fuel. The greenhouse gas emission savings associated with that excess electricity shall be taken to be equal to the amount of greenhouse gas that would be emitted when an equal amount of electricity was generated in a power plant using the same fuel as the cogeneration unit. |
|
17. |
Where a fuel production process produces, in combination, the fuel for which emissions are being calculated and one or more other products (co-products), greenhouse gas emissions shall be divided between the fuel or its intermediate product and the co-products in proportion to their energy content (determined by lower heating value in the case of co-products other than electricity). |
|
18. |
For the purposes of the calculation referred to in point 17, the emissions to be divided shall be eec + el + those fractions of ep , etd and eee that take place up to and including the process step at which a co-product is produced. If any allocation to co-products has taken place at an earlier process step in the life-cycle, the fraction of those emissions assigned in the last such process step to the intermediate fuel product shall be used for this purpose instead of the total of those emissions. All co-products, including electricity that does not fall under the scope of point 16, shall be taken into account for the purposes of that calculation, except for agricultural crop residues, including straw, bagasse, husks, cobs and nut shells. Co-products that have a negative energy content shall be considered to have an energy content of zero for the purpose of the calculation. Wastes, agricultural crop residues, including straw, bagasse, husks, cobs and nut shells, and residues from processing, including crude glycerine (glycerine that is not refined), shall be considered to have zero life-cycle greenhouse gas emissions up to the process of collection of those materials. In the case of fuels produced in refineries, the unit of analysis for the purposes of the calculation referred to in point 17 shall be the refinery. |
|
19. |
For the purposes of the calculation referred to in point 4, the fossil fuel comparator EF shall be the latest available actual average emissions from the fossil part of petrol and diesel consumed in the Community as reported under this Directive. If no such data are available, the value used shall be 83,8 gCO2eq/MJ. |
D. Disaggregated default values for biofuels
Disaggregated default values for cultivation: ‘eec ’ as defined in Part C of this Annex
|
Biofuel production pathway |
Typical greenhouse gas emissions (gCO2eq/MJ) |
Default greenhouse gas emissions (gCO2eq/MJ) |
|
Sugar beet ethanol |
12 |
12 |
|
Wheat ethanol |
23 |
23 |
|
Corn (maize) ethanol, Community produced |
20 |
20 |
|
Sugar cane ethanol |
14 |
14 |
|
The part from renewable sources of ETBE |
Equal to that of the ethanol production pathway used |
|
|
The part from renewable sources of TAEE |
Equal to that of the ethanol production pathway used |
|
|
Rape seed biodiesel |
29 |
29 |
|
Sunflower biodiesel |
18 |
18 |
|
Soybean biodiesel |
19 |
19 |
|
Palm oil biodiesel |
14 |
14 |
|
Waste vegetable or animal (*1) oil biodiesel |
0 |
0 |
|
Hydrotreated vegetable oil from rape seed |
30 |
30 |
|
Hydrotreated vegetable oil from sunflower |
18 |
18 |
|
Hydrotreated vegetable oil from palm oil |
15 |
15 |
|
Pure vegetable oil from rape seed |
30 |
30 |
|
Biogas from municipal organic waste as compressed natural gas |
0 |
0 |
|
Biogas from wet manure as compressed natural gas |
0 |
0 |
|
Biogas from dry manure as compressed natural gas |
0 |
0 |
|
(*1)
Not including animal oil produced from animal by-products classified as category 3 material in accordance with Regulation (EC) No 1774/2002. |
||
Disaggregated default values for processing (including excess electricity): ‘ep – eee ’ as defined in Part C of this Annex
|
Biofuel production pathway |
Typical greenhouse gas emissions (gCO2eq/MJ) |
Default greenhouse gas emissions (gCO2eq/MJ) |
|
Sugar beet ethanol |
19 |
26 |
|
Wheat ethanol (process fuel not specified) |
32 |
45 |
|
Wheat ethanol (lignite as process fuel in CHP plant) |
32 |
45 |
|
Wheat ethanol (natural gas as process fuel in conventional boiler) |
21 |
30 |
|
Wheat ethanol (natural gas as process fuel in CHP plant) |
14 |
19 |
|
Wheat ethanol (straw as process fuel in CHP plant) |
1 |
1 |
|
Corn (maize) ethanol, Community produced (natural gas as process fuel in CHP plant) |
15 |
21 |
|
Sugar cane ethanol |
1 |
1 |
|
The part from renewable sources of ETBE |
Equal to that of the ethanol production pathway used |
|
|
The part from renewable sources of TAEE |
Equal to that of the ethanol production pathway used |
|
|
Rape seed biodiesel |
16 |
22 |
|
Sunflower biodiesel |
16 |
22 |
|
Soybean biodiesel |
18 |
26 |
|
Palm oil biodiesel (process not specified) |
35 |
49 |
|
Palm oil biodiesel (process with methane capture at oil mill) |
13 |
18 |
|
Waste vegetable or animal oil biodiesel |
9 |
13 |
|
Hydrotreated vegetable oil from rape seed |
10 |
13 |
|
Hydrotreated vegetable oil from sunflower |
10 |
13 |
|
Hydrotreated vegetable oil from palm oil (process not specified) |
30 |
42 |
|
Hydrotreated vegetable oil from palm oil (process with methane capture at oil mill) |
7 |
9 |
|
Pure vegetable oil from rape seed |
4 |
5 |
|
Biogas from municipal organic waste as compressed natural gas |
14 |
20 |
|
Biogas from wet manure as compressed natural gas |
8 |
11 |
|
Biogas from dry manure as compressed natural gas |
8 |
11 |
Disaggregated default values for transport and distribution: ‘etd ’ as defined in Part C of this Annex
|
Biofuel production pathway |
Typical greenhouse gas emissions (gCO2eq/MJ) |
Default greenhouse gas emissions (gCO2eq/MJ) |
|
Sugar beet ethanol |
2 |
2 |
|
Wheat ethanol |
2 |
2 |
|
Corn (maize) ethanol, Community produced |
2 |
2 |
|
Sugar cane ethanol |
9 |
9 |
|
The part from renewable sources of ETBE |
Equal to that of the ethanol production pathway used |
|
|
The part from renewable sources of TAEE |
Equal to that of the ethanol production pathway used |
|
|
Rape seed biodiesel |
1 |
1 |
|
Sunflower biodiesel |
1 |
1 |
|
Soybean biodiesel |
13 |
13 |
|
Palm oil biodiesel |
5 |
5 |
|
Waste vegetable or animal oil biodiesel |
1 |
1 |
|
Hydrotreated vegetable oil from rape seed |
1 |
1 |
|
Hydrotreated vegetable oil from sunflower |
1 |
1 |
|
Hydrotreated vegetable oil from palm oil |
5 |
5 |
|
Pure vegetable oil from rape seed |
1 |
1 |
|
Biogas from municipal organic waste as compressed natural gas |
3 |
3 |
|
Biogas from wet manure as compressed natural gas |
5 |
5 |
|
Biogas from dry manure as compressed natural gas |
4 |
4 |
Total for cultivation, processing, transport and distribution
|
Biofuel production pathway |
Typical greenhouse gas emissions (gCO2eq/MJ) |
Default greenhouse gas emissions (gCO2eq/MJ) |
|
Sugar beet ethanol |
33 |
40 |
|
Wheat ethanol (process fuel not specified) |
57 |
70 |
|
Wheat ethanol (lignite as process fuel in CHP plant) |
57 |
70 |
|
Wheat ethanol (natural gas as process fuel in conventional boiler) |
46 |
55 |
|
Wheat ethanol (natural gas as process fuel in CHP plant) |
39 |
44 |
|
Wheat ethanol (straw as process fuel in CHP plant) |
26 |
26 |
|
Corn (maize) ethanol, Community produced (natural gas as process fuel in CHP plant) |
37 |
43 |
|
Sugar cane ethanol |
24 |
24 |
|
The part from renewable sources of ETBE |
Equal to that of the ethanol production pathway used |
|
|
The part from renewable sources of TAEE |
Equal to that of the ethanol production pathway used |
|
|
Rape seed biodiesel |
46 |
52 |
|
Sunflower biodiesel |
35 |
41 |
|
Soybean biodiesel |
50 |
58 |
|
Palm oil biodiesel (process not specified) |
54 |
68 |
|
Palm oil biodiesel (process with methane capture at oil mill) |
32 |
37 |
|
Waste vegetable or animal oil biodiesel |
10 |
14 |
|
Hydrotreated vegetable oil from rape seed |
41 |
44 |
|
Hydrotreated vegetable oil from sunflower |
29 |
32 |
|
Hydrotreated vegetable oil from palm oil (process not specified) |
50 |
62 |
|
Hydrotreated vegetable oil from palm oil (process with methane capture at oil mill) |
27 |
29 |
|
Pure vegetable oil from rape seed |
35 |
36 |
|
Biogas from municipal organic waste as compressed natural gas |
17 |
23 |
|
Biogas from wet manure as compressed natural gas |
13 |
16 |
|
Biogas from dry manure as compressed natural gas |
12 |
15 |
E. Estimated disaggregated default values for future biofuels that were not on the market or were only on the market in negligible quantities in January 2008
Disaggregated values for cultivation: ‘eec ’ as defined in Part C of this Annex
|
Biofuel production pathway |
Typical greenhouse gas missions (gCO2eq/MJ) |
Default greenhouse gas emissions (gCO2eq/MJ) |
|
Wheat straw ethanol |
3 |
3 |
|
Waste wood ethanol |
1 |
1 |
|
Farmed wood ethanol |
6 |
6 |
|
Waste wood Fischer-Tropsch diesel |
1 |
1 |
|
Farmed wood Fischer-Tropsch diesel |
4 |
4 |
|
Waste wood DME |
1 |
1 |
|
Farmed wood DME |
5 |
5 |
|
Waste wood methanol |
1 |
1 |
|
Farmed wood methanol |
5 |
5 |
|
The part from renewable sources of MTBE |
Equal to that of the methanol production pathway used |
|
Disaggregated values for processing (including excess electricity): ‘ep – eee ’ as defined in Part C of this Annex
|
Biofuel production pathway |
Typical greenhouse gas emissions (gCO2eq/MJ) |
Default greenhouse gas emissions (gCO2eq/MJ) |
|
Wheat straw ethanol |
5 |
7 |
|
Wood ethanol |
12 |
17 |
|
Wood Fischer-Tropsch diesel |
0 |
0 |
|
Wood DME |
0 |
0 |
|
Wood methanol |
0 |
0 |
|
The part from renewable sources of MTBE |
Equal to that of the methanol production pathway used |
|
Disaggregated values for transport and distribution: ‘etd ’ as defined in Part C of this Annex
|
Biofuel production pathway |
Typical greenhouse gas emissions (gCO2eq/MJ) |
Default greenhouse gas emissions (gCO2eq/MJ) |
|
Wheat straw ethanol |
2 |
2 |
|
Waste wood ethanol |
4 |
4 |
|
Farmed wood ethanol |
2 |
2 |
|
Waste wood Fischer-Tropsch diesel |
3 |
3 |
|
Farmed wood Fischer-Tropsch diesel |
2 |
2 |
|
Waste wood DME |
4 |
4 |
|
Farmed wood DME |
2 |
2 |
|
Waste wood methanol |
4 |
4 |
|
Farmed wood methanol |
2 |
2 |
|
The part from renewable sources of MTBE |
Equal to that of the methanol production pathway used |
|
Total for cultivation, processing, transport and distribution
|
Biofuel production pathway |
Typical greenhouse gas emissions (gCO2eq/MJ) |
Default greenhouse gas emissions (gCO2eq/MJ) |
|
Wheat straw ethanol |
11 |
13 |
|
Waste wood ethanol |
17 |
22 |
|
Farmed wood ethanol |
20 |
25 |
|
Waste wood Fischer-Tropsch diesel |
4 |
4 |
|
Farmed wood Fischer-Tropsch diesel |
6 |
6 |
|
Waste wood DME |
5 |
5 |
|
Farmed wood DME |
7 |
7 |
|
Waste wood methanol |
5 |
5 |
|
Farmed wood methanol |
7 |
7 |
|
The part from renewable sources of MTBE |
Equal to that of the methanol production pathway used |
|
ANNEX V
Part A. Provisional estimated indirect land-use change emissions from biofuels (gCO2eq/MJ) ( 15 )
|
Feedstock group |
Mean (1) |
Interpercentile range derived from the sensitivity analysis (2) |
|
Cereals and other starch-rich crops |
12 |
8 to 16 |
|
Sugars |
13 |
4 to 17 |
|
Oil crops |
55 |
33 to 66 |
|
(1)
The mean values included here represent a weighted average of the individually modelled feedstock values.
(2)
The range included here reflects 90 % of the results using the fifth and ninety-fifth percentile values resulting from the analysis. The fifth percentile suggests a value below which 5 % of the observations were found (i.e. 5 % of total data used showed results below 8, 4, and 33 gCO2eq/MJ). The ninety-fifth percentile suggests a value below which 95 % of the observations were found (i.e. 5 % of total data used showed results above 16, 17, and 66 gCO2eq/MJ). |
||
Part B. Biofuels for which the estimated indirect land-use change emissions are considered to be zero
Biofuels produced from the following feedstock categories will be considered to have estimated indirect land-use change emissions of zero:
feedstocks which are not listed under Part A of this Annex.
feedstocks, the production of which has led to direct land-use change, i.e. a change from one of the following IPCC land cover categories; forest land, grassland, wetlands, settlements, or other land, to cropland or perennial cropland ( 16 ). In such a case a direct land-use change emission value (el ) should have been calculated in accordance with paragraph 7 of Part C of Annex IV.
( 1 ) The numbering of these CN codes as specified in the CCT, as amended by Commission Regulation (EC) No 2031/2001 (OJ L 279, 23.10.2001, p. 1).
( 2 ) The numbering of these CN codes as specified in the Common Customs Tariff (OJ L 256, 7.6.1987, p. 1).
( 3 ) OJ L 164, 30.6.1994, p. 15.
( 4 ) OJ L 59, 27.2.1998, p. 1.
( 5 ) OJ L 173, 12.7.2000, p. 1.
( 6 ) OJ L 140, 5.6.2009, p. 16.
( 7 ) OJ L 275, 25.10.2003, p. 32.
( 8 ) OJ L 30, 31.1.2009, p. 16.
( 9 ) OJ L 154, 21.6.2003, p. 1.
( 10 ) OJ L 327, 22.12.2000, p. 1.
( 11 ) Regulation (EU) No 182/2011 of the European Parliament and of the Council of 16 February 2011 laying down the rules and general principles concerning mechanisms for control by Member States of the Commission's exercise of implementing powers (OJ L 55, 28.2.2011, p. 13).
( 12 ) The quotient obtained by dividing the molecular weight of CO2 (44,010 g/mol) by the molecular weight of carbon (12,011 g/mol) is equal to 3,664.
( 13 ) Cropland as defined by IPCC.
( 14 ) Perennial crops are defined as multi-annual crops, the stem of which is usually not annually harvested such as short rotation coppice and oil palm.
( 15 )
(+) The mean values reported here represent a weighted average of the individually modelled feedstock values. The magnitude of the values in the Annex is sensitive to the range of assumptions (such as treatment of co-products, yield developments, carbon stocks and displacement of other commodities) used in the economic models developed for their estimation. Although it is therefore not possible to fully characterise the uncertainty range associated with such estimates, a sensitivity analysis conducted on the results based on a random variation of key parameters, a so-called Monte Carlo analysis, was conducted.
( 16 )
(++) Perennial crops are defined as multi-annual crops, the stem of which is usually not annually harvested such as short rotation coppice and oil palm.