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Commission Regulation (EU) No 601/2012 of 21 June 2012 on the monitoring and reporting of greenhouse gas emissions pursuant to Directive 2003/87/EC of the European Parliament and of the Council Text with EEA relevance

Commission Regulation (EU) No 601/2012 of 21 June 2012 on the monitoring and reporting of greenhouse gas emissions pursuant to Directive 2003/87/EC of the European Parliament and of the Council Text with EEA relevance

THE EUROPEAN COMMISSION,

Having regard to the Treaty of the Functioning of the European Union,

Having regard to 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 and amending Council Directive 96/61/EC(1) and in particular Article 14(1) thereof,

Whereas:

  1. The complete, consistent, transparent and accurate monitoring and reporting of greenhouse gas emissions, in accordance with the harmonised requirements laid down in this Regulation, are fundamental for the effective operation of the greenhouse gas emission allowance trading scheme established pursuant to Directive 2003/87/EC. During the second compliance cycle of the greenhouse gas emissions trading scheme, covering the years 2008 to 2012, industrial operators, aviation operators, verifiers and competent authorities have gained experience with monitoring and reporting pursuant to Commission Decision 2007/589/EC of 18 July 2007 establishing guidelines for the monitoring and reporting of greenhouse gas emissions pursuant to Directive 2003/87/EC of the European Parliament and of the Council(2). The rules for the third trading period of the Union’s greenhouse gas emission allowance trading scheme which begins on 1 January 2013 and for the following trading periods should build on that experience.

  2. The definition of biomass in this Regulation should be consistent with the definition of the terms ‘biomass’, ‘bioliquids’ and ‘biofuels’ set out in Article 2 of 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 and amending and subsequently repealing Directives 2001/77/EC and 2003/30/EC(3), in particular since preferential treatment with regard to allowance surrender obligations under the Union’s greenhouse gas emission allowance trading scheme pursuant to Directive 2003/87/EC constitutes a ‘support scheme’ within the meaning of Article 2(k) and consequently financial support within the meaning of Article 17(1)(c) of Directive 2009/28/EC.

  3. For reasons of consistency, definitions laid down in Commission Decision 2009/450/EC of 8 June 2009 on the detailed interpretation of the aviation activities listed in Annex I to Directive 2003/87/EC of the European Parliament and of the Council(4) and Directive 2009/31/EC of the European Parliament and of the Council of 23 April 2009 on the geological storage of carbon dioxide and amending Council Directive 85/337/EEC, European Parliament and Council Directives 2000/60/EC, 2001/80/EC, 2004/35/EC, 2006/12/EC, 2008/1/EC and Regulation (EC) No 1013/2006(5) should apply to this Regulation.

  4. To make the operation of the monitoring and reporting system optimal, the Member States which designate more than one competent authority should ensure that those competent authorities coordinate their work in line with the principles set out in this Regulation.

  5. The monitoring plan, setting out detailed, complete and transparent documentation concerning the methodology of a specific installation or aircraft operator should be a core element of the system established by this Regulation. Regular updates of the plan should be required, both to respond to the verifier’s findings and on the basis of the operator’s or aircraft operator’s own initiative. The main responsibility for the implementation of the monitoring methodology, parts of which are specified by procedures required by this Regulation, should remain with the operator or the aircraft operator.

  6. It is necessary to establish basic monitoring methodologies to minimise the burden on operators and aircraft operators and facilitate the effective monitoring and reporting of greenhouse gas emissions pursuant to Directive 2003/87/EC. Those methodologies should include basic calculation and measurement methodologies. The calculation methodologies should be further differentiated into a standard methodology and a mass balance methodology. Flexibility should be provided to allow a combination of measurement methodologies, standard calculation methodology and mass balance within the same installation, provided the operator ensures that omissions or double counting do not occur.

  7. To further minimise the burden on operators and aircraft operators, simplification with regard to the uncertainty assessment requirement, without reducing accuracy, should be introduced. Considerably reduced requirements with regard to uncertainty assessment should be applied where measuring instruments are used under type-conform conditions, in particular where measuring instruments are under national legal metrological control.

  8. It is necessary to define calculation factors which can be either default factors or determined by analysis. Requirements for analysis should retain the preference for use of laboratories accredited in accordance with the harmonised standard General requirements for the competence of testing and calibration laboratories (EN ISO/IEC 17025) for the relevant analytical methods, and introduce more pragmatic requirements for demonstrating robust equivalence in the case of non-accredited laboratories, including in conformity with the harmonised standard Quality management systems – Requirements (EN ISO/IEC 9001) or other relevant certified quality management systems.

  9. A more transparent and consistent manner of determining unreasonable costs should be laid down.

  10. The measurement-based methodology should be set on a more equal footing with the calculation-based methodology in order to recognise the increased confidence in continuous emissions monitoring systems and underpinning quality assurance. That requires more proportional requirements concerning cross-checks with calculations as well as the clarification of data handling and other quality assurance requirements.

  11. Imposing a disproportionate monitoring effort on installations with lower, less consequential annual emissions should be avoided, while ensuring that an acceptable level of accuracy is maintained. In that regard, special conditions for installations considered having low emissions and for aircraft operators considered small emitters should be set out.

  12. Article 27 of Directive 2003/87/EC allows Member States to exclude small installations, subject to equivalent measures, from the Union’s greenhouse gas emission allowance trading scheme provided that the conditions contained in that Article are met. This Regulation should not apply directly to those installations excluded pursuant to Article 27 of Directive 2003/87/EC unless the Member State decides that this Regulation should apply.

  13. To close potential loopholes connected to the transfer of inherent or pure CO2, such transfers should only be allowed subject to very specific conditions. Those conditions are that the transfer of inherent CO2 should only be to other EU-ETS installations and the transfer of pure CO2 should only occur for the purposes of storage in a geological storage site pursuant to the Union’s greenhouse gas emission allowance trading scheme, which is at present the only form of permanent storage of CO2 accepted under the Union’s greenhouse gas emission trading scheme. Those conditions should not, nevertheless, exclude the possibility of future innovations.

  14. Specific aviation-related provisions on monitoring plans and monitoring of greenhouse gas emissions should be laid down. One provision should be the determination of density by onboard measurement and by fuel invoices as equivalent options. Another provision should be the raising of the threshold for consideration of an aircraft operator as a small emitter from 10 000 tonnes of CO2 emissions per year to 25 000 tonnes of CO2 per year.

  15. The estimation of missing data should be made more consistent, by requiring the use of conservative estimation procedures recognised in the monitoring plan or, where this is not possible, through the approval by the competent authority and the inclusion of an appropriate procedure in the monitoring plan.

  16. The implementation of the improvement principle requiring operators to regularly review their monitoring methodology for improvement and to consider recommendations made by verifiers as part of the verification process should be strengthened. Where a methodology is used, which is not based on tiers, or where the highest tier methodologies are not met, operators should regularly report on the steps being taken to meet a monitoring methodology based on the tier system and to reach the highest tier required.

  17. Aircraft operators may, pursuant to Article 3e(1) of Directive 2003/87/EC, apply for an allocation of emission allowances free of charge, in respect of activities listed in Annex I to that Directive, based on verified tonne-kilometre data. However, in the light of the principle of proportionality, where an aircraft operator is objectively unable to provide verified tonne-kilometre data by the relevant deadline because of serious and unforeseeable circumstances outside of its control, that aircraft operator should be able to submit the best tonne-kilometre data available, provided the necessary safeguards are in place.

  18. The use of information technology, including requirements for data exchange formats and the use of automated systems, should be promoted and the Member States should be therefore allowed to require the economic operators to use such systems. The Member States should be also allowed to elaborate electronic templates and file format specifications which should, however, conform to minimum standards published by the Commission.

  19. Decision 2007/589/EC should be repealed. However, the effects of its provisions should be maintained for the monitoring, reporting and verification of the emissions and activity data occurring during the first and second trading periods of the Union’s greenhouse gas emission allowance trading scheme.

  20. Member States should be provided sufficient time to adopt the necessary measures and establish the appropriate national institutional framework to ensure the effective application of this Regulation. This Regulation should therefore apply from the date of the beginning of the third trading period.

  21. The measures provided for in this Regulation are in accordance with the opinion of the Climate Change Committee,

HAS ADOPTED THIS REGULATION:

CHAPTER I GENERAL PROVISIONS

SECTION 1 Subject matter and definitions

Article 1 Subject matter

This Regulation lays down rules for the monitoring and reporting of greenhouse gas emissions and activity data pursuant to Directive 2003/87/EC in the trading period of the Union emissions trading scheme commencing on 1 January 2013 and subsequent trading periods.

Article 2 Scope

This Regulation shall apply to the monitoring and reporting of greenhouse gas emissions specified in relation to the activities listed in Annex I to Directive 2003/87/EC and activity data from stationary installations, from aviation activities and to the monitoring and reporting of tonne-kilometre data from aviation activities.

It shall apply to emissions and activity data occurring from 1 January 2013.

Article 3 Definitions

SECTION 2 General principles

Article 4 General obligation

Article 5 Completeness

Article 6 Consistency, comparability and transparency

Article 7 Accuracy

Article 8 Integrity of methodology

Article 9 Continuous improvement

Article 10 Coordination

CHAPTER II MONITORING PLAN

SECTION 1 General rules

Article 11 General obligation

Article 12 Content and submission of the monitoring plan

Article 13 Standardised and simplified monitoring plans

Article 14 Modifications of the monitoring plan

Article 15 Approval of modifications of the monitoring plan

Article 16 Implementation and recordkeeping of modifications

SECTION 2 Technical feasibility and unreasonable costs

Article 17 Technical feasibility

Article 18 Unreasonable costs

CHAPTER III MONITORING OF EMISSIONS OF STATIONARY INSTALLATIONS

SECTION 1 General provisions

Article 19 Categorisation of installations and source streams

Article 20 Monitoring boundaries

Article 21 Choice of the monitoring methodology

Article 22 Monitoring methodology not based on tiers

Article 23 Temporary changes to the monitoring methodology

SECTION 2 Calculation-based methodology

Subsection 1 General

Article 24 Calculation of emissions under the standard methodology
Article 25 Calculation of emissions under the mass balance methodology
Article 26 Applicable tiers

Subsection 2 Activity data

Article 27 Determination of activity data
Article 28 Measurement systems under the operator’s control
Article 29 Measurement systems outside the operator’s own control

Subsection 3 Calculation factors

Article 30 Determination of calculation factors
Article 31 Default values for calculation factors
Article 32 Calculation factors based on analyses
Article 33 Sampling plan
Article 34 Use of laboratories
Article 35 Frequencies for analyses

Subsection 4 Specific calculation factors

Article 36 Emission factors for CO2
Article 37 Oxidation and conversion factors

Subsection 5 Treatment of biomass

Article 38 Biomass source streams
Article 39 Determination of biomass and fossil fraction

SECTION 3 Measurement-based methodology

Article 40 Use of the measurement-based monitoring methodology

Article 41 Tier requirements

Article 42 Measurement standards and laboratories

Article 43 Determination of emissions

Article 44 Data aggregation

Article 45 Missing data

Article 46 Corroborating with calculation of emissions

SECTION 4 Special provisions

Article 47 Installations with low emissions

Article 48 Inherent CO2

Article 49 Transferred CO2

CHAPTER IV MONITORING OF EMISSIONS AND TONNE-KILOMETRE DATA FROM AVIATION

Article 50 General provisions

Article 51 Submission of monitoring plans

Article 52 Monitoring methodology for emissions from aviation activities

Article 53 Specific provisions for biomass

Article 54 Small emitters

Article 55 Sources of uncertainty

Article 56 Determination of tonne-kilometre data

CHAPTER V DATA MANAGEMENT AND CONTROL

Article 57 Data flow activities

Article 58 Control system

Article 59 Quality assurance

Article 60 Quality assurance of information technology

Article 61 Segregation of duties

Article 62 Internal reviews and validation of data

Article 63 Corrections and corrective action

Article 64 Out-sourced processes

Article 65 Treatment of data gaps

Article 66 Records and documentation

CHAPTER VI REPORTING REQUIREMENTS

Article 67 Timing and obligations for reporting

Article 68 Force majeure

Article 69 Reporting on improvements to the monitoring methodology

Article 70 Determination of emissions by the competent authority

Article 71 Access to information

Article 72 Rounding of data

Article 73 Ensuring consistency with other reporting

CHAPTER VII INFORMATION TECHNOLOGY REQUIREMENTS

Article 74 Electronic data exchange formats

Article 75 Use of automated systems

CHAPTER VIII FINAL PROVISIONS

Article 76 Repeal of Decision 2007/589/EC and transitional provisions

Article 77 Entry into force

ANNEX I

ANNEX II

ANNEX III

ANNEX IV

ANNEX V

ANNEX VI

ANNEX VII

ANNEX VIII

ANNEX IX

ANNEX X