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gas emissions pursuant to Directive 2003/87/EC of the European Parliament and of the Council (Text with EEA relevance) (repealed)
EU Regulation No 601/2012 · Adopted 21 June 2012 · Extends to United Kingdom
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(Text with EEA relevance) (repealed)
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/ECf1 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 Councilf2. 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/ECf3, 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 Councilf4 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 1013/2006f5 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:
Annotations to the whole text
Footnotes
Contents
- Chapter I: GENERAL PROVISIONS
- Subject matter and definitions
- 1Subject matter
- 2Scope
- 3Definitions
- General principles
- 4General obligation
- 5Completeness
- 6Consistency, comparability and transparency
- 7Accuracy
- 8Integrity of methodology
- 9Continuous improvement
- 10Coordination
- Chapter II: MONITORING PLAN
- General rules
- 11General obligation
- 12Content and submission of the monitoring plan
- 13Standardised and simplified monitoring plans
- 14Modifications of the monitoring plan
- 15Approval of modifications of the monitoring plan
- 16Implementation and recordkeeping of modifications
- Technical feasibility and unreasonable costs
- 17Technical feasibility
- 18Unreasonable costs
- Chapter III: MONITORING OF EMISSIONS OF STATIONARY INSTALLATIONS
- General provisions
- 19Categorisation of installations and source streams
- 20Monitoring boundaries
- 21Choice of the monitoring methodology
- 22Monitoring methodology not based on tiers
- 23Temporary changes to the monitoring methodology
- Calculation-based methodology
- General
- 24Calculation of emissions under the standard methodology
- 25Calculation of emissions under the mass balance methodology
- 26Applicable tiers
- Activity data
- 27Determination of activity data
- 28Measurement systems under the operator’s control
- 29Measurement systems outside the operator’s own control
- Calculation factors
- 30Determination of calculation factors
- 31Default values for calculation factors
- 32Calculation factors based on analyses
- 33Sampling plan
- 34Use of laboratories
- 35Frequencies for analyses
- Specific calculation factors
- 36Emission factors for CO2
- 37Oxidation and conversion factors
- Treatment of biomass
- 38Biomass source streams
- 39Determination of biomass and fossil fraction
- Measurement-based methodology
- 40Use of the measurement-based monitoring methodology
- 41Tier requirements
- 42Measurement standards and laboratories
- 43Determination of emissions
- 44Data aggregation
- 45Missing data
- 46Corroborating with calculation of emissions
- Special provisions
- 47Installations with low emissions
- 48Inherent CO2
- 49Transferred CO 2
- Chapter IV: MONITORING OF EMISSIONS AND TONNE-KILOMETRE DATA FROM AVIATION
- 50General provisions
- 51Submission of monitoring plans
- 52Monitoring methodology for emissions from aviation activities
- 53Specific provisions for biomass
- 54Small emitters
- 55Sources of uncertainty
- 56Determination of tonne-kilometre data
- Chapter V: DATA MANAGEMENT AND CONTROL
- 57Data flow activities
- 58Control system
- 59Quality assurance
- 60Quality assurance of information technology
- 61Segregation of duties
- 62Internal reviews and validation of data
- 63Corrections and corrective action
- 64Out-sourced processes
- 65Treatment of data gaps
- 66Records and documentation
- Chapter VI: REPORTING REQUIREMENTS
- 67Timing and obligations for reporting
- 68Force majeure
- 69Reporting on improvements to the monitoring methodology
- 70Determination of emissions by the competent authority
- 71Access to information
- 72Rounding of data
- 73Ensuring consistency with other reporting
- Chapter VII: INFORMATION TECHNOLOGY REQUIREMENTS
- 74Electronic data exchange formats
- 75Use of automated systems
- Chapter VIII: FINAL PROVISIONS
- 76Repeal of Decision 2007/589/EC and transitional provisions
- 77Entry into force
- Signature
- Annex I: Minimum content of the monitoring plan (Article 12(1))
- 1Minimum content of the monitoring plan for installations
- Minimum content of monitoring plans for aviation emissions
- 1The monitoring plan shall contain the following information for all aircraft operators:
- 2The monitoring plan shall contain the following information for aircraft operators which are not small emitters in accordance with Article 54(1) or which do not intend to use a small emitter tool in accordance with Article 54(2):
- 3Minimum content of monitoring plans for tonne-kilometre data
- Annex II: Tier thresholds for calculation-based methodologies related to installations (Article 12(1))
- 1Definition of tiers for activity data
- 2Definition of tiers for calculation factors for combustion emissions
- 2.1Tiers for emission factors
- 2.2Tiers for net calorific value (NCV)
- 2.3Tiers for oxidation factors
- 2.4Tiers for biomass fraction
- 3Definition of tiers for calculation factors for mass balances
- 3.1Tiers for carbon content
- 3.2Tiers for net calorific values
- 4Definition of tiers for the calculation factors for process emissions from carbonate decomposition
- 4.1Tiers for the emission factor using Method A
- 4.2Tiers for the conversion factor using Method A
- 4.3Tiers for the emission factor using Method B
- 4.4Tiers for the conversion factor using Method B
- Annex III: Monitoring methodologies for aviation (Article 52 and Article 56)
- Calculation methodologies for the determination of GHGs in the aviation sector
- Method A
- Method B
- 2Tier levels for fuel consumption Repealed
- 3Emission factors for standard fuels
- 4Calculation of Great Circle Distance
- Annex IV: Activity-specific monitoring methodologies related to installations (Article 20(2))
- Specific monitoring rules for emissions from combustion processes
- AScope
- BSpecific monitoring rules
- CFlue gas scrubbing
- Method A:Emission factor
- Method B:Emission factor
- DFlares
- Refining of Mineral Oil as Listed in Annex I to Directive 2003/87/EC
- AScope
- BSpecific monitoring rules
- Production of coke as listed in Annex I to Directive 2003/87/EC
- AScope
- BSpecific monitoring rules
- Metal ore roasting and sintering as listed in Annex I to Directive 2003/87/EC
- AScope
- BSpecific monitoring rules
- Production of pig iron and steel as listed in Annex I to Directive 2003/87/EC
- AScope
- BSpecific monitoring rules
- Production or processing of ferrous and non-ferrous metals as listed in Annex I to Directive 2003/87/EC
- AScope
- BSpecific monitoring rules
- CO2 Emissions from production or processing of primary aluminium as listed in Annex I to Directive 2003/87/EC
- AScope
- BSpecific monitoring rules
- PFC emissions from production or processing of primary aluminium as listed in Annex I to Directive 2003/87/EC
- AScope
- BDetermination of PFC emissions
- Calculation Method A —Slope Method
- Calculation Method B —Overvoltage Method
- CDetermination of CO2(e) emissions
- Production of cement clinker as listed in Annex I to Directive 2003/87/EC
- AScope
- BSpecific monitoring rules
- Calculation Method A:Kiln Input Based
- Calculation Method B:Clinker Output Based
- CEmissions related to discarded dust
- DEmissions from non-carbonate carbon in raw meal
- Production of lime or calcination of dolomite or magnesite as listed in Annex I to Directive 2003/87/EC
- AScope
- BSpecific monitoring rules
- Manufacture of glass, glass fibre or mineral wool insulation material as listed in Annex I to Directive 2003/87/EC
- AScope
- BSpecific monitoring rules
- Manufacture of ceramic products as listed in Annex I to Directive 2003/87/EC
- AScope
- BSpecific monitoring rules
- Method A (Input based)
- Method B (Output based)
- Production of gypsum products and plaster boards as listed in Annex I to Directive 2003/87/EC
- AScope
- BSpecific monitoring rules
- Pulp and paper production as listed in Annex I to Directive 2003/87/EC
- AScope
- BSpecific monitoring rules
- Production of carbon black as listed in Annex I to Directive 2003/87/EC
- AScope
- BSpecific monitoring rules
- Determination of nitrous oxide (N2O) emissions from nitric acid, adipic acid, caprolactam, glyoxal and glyoxylic acid production as listed in Annex I to Directive 2003/87/EC
- AScope
- Determination of N2O emissions
- B.1Annual N2O emissions
- B.2Hourly N2O emissions
- B.3Determination of flue gas flow
- B.4Oxygen (O2) concentrations
- B.5Calculation of N2O emissions
- B.6Determination of activity production rates
- B.7Sampling rates
- CDetermination of annual CO2 equivalent — CO2(e)
- Production of ammonia as listed in Annex I to Directive 2003/87/EC
- AScope
- BSpecific monitoring rules
- Production of bulk organic chemicals as listed in Annex I to Directive 2003/87/EC
- AScope
- BSpecific monitoring rules
- Production of hydrogen and synthesis gas as listed in Annex I to Directive 2003/87/EC
- AScope
- BSpecific monitoring rules
- Production of soda ash and sodium bicarbonate as listed in Annex I to Directive 2003/87/EC
- AScope
- BSpecific monitoring rules
- Determination of greenhouse gas emissions from CO2 capture activities for the purposes of transport and geological storage in a storage site permitted under Directive 2009/31/EC
- AScope
- Quantification of transferred and emitted CO2 amounts
- B.1Installation level quantification
- B.2Determination of transferred CO2
- Determination of greenhouse gas emissions from the transport of CO2 by pipelines for geological storage in a storage site permitted under Directive 2009/31/EC
- AScope
- BQuantification methodologies for CO2
- B.1Method A
- B.2Method B
- B.2.1Fugitive emissions from the transport network
- B.2.2Emissions from leakage events
- B.2.3Vented emissions
- Geological storage of CO2 in a storage site permitted under Directive 2009/31/EC
- AScope
- BQuantification of CO2 emissions
- B.1Vented and fugitive emissions from injection
- B.2Vented and fugitive emissions from enhanced hydrocarbon recovery operations
- B.3Leakage from the storage complex
- Annex VMinimum tier requirements for calculation-based methodologies involving Category A installations and calculation factors for commercial standard fuels used by Category B and C installations (Article 26(1))
- Annex VI: Reference values for calculation factors (Article 31(1)(a))
- 1Fuel emission factors related to net calorific values (NCV)
- 2Emission factors related to process emissions
- 3Global warming potentials for non-CO2 greenhouse gases
- Annex VIIAnnex VII
- Annex VIII: Measurement-based methodologies (Article 41)
- 1Tier definitions for measurement-based methodologies
- 2Minimum requirements
- Determination of GHGs using measurement-based methodologies
- Equation 1:Calculation of Annual Emissions
- Calculation of the concentration using indirect concentration measurement
- Equation 3:Calculation of the concentration
- Substitution for missing concentration data for measurement-based methodologies
- Equation 4:Substitution for missing data for measurement-based methodologies
- Annex IXMinimum data and information to be retained in accordance with Article 66(1)
- 1Common elements for installations and aircraft operators
- 2Specific elements for stationary source installations
- 3Specific elements for aviation activities
- Annex X: Minimum content of Annual Reports (Article 67(3))
- 1Annual emission reports of stationary source installations
- 2Annual emission reports of aircraft operators
- 3Tonne-kilometre data reports of aircraft operators