LeX-Ray
Monitoring Reporting and Verification of Carbon Dioxide Emissions from Maritime Transport Regulation
Article 1: Subject matter
Article 2: Scope
Article 3: Definitions
Article 4: Common principles for monitoring and reporting
Article 5: Methods for monitoring CO2emissions and other relevant information
Article 6: Content and submission of the monitoring plan
Article 7: Modifications of the monitoring plan
Article 8: Monitoring of activities within a reporting period
Article 9: Monitoring on a per-voyage basis
Article 10: Monitoring on an annual basis
Companies may also monitor fuel consumed and CO 2 emitted, differentiating on the basis of other criteria defined in the monitoring plan. 2
Article 11: Content of the emissions report
Article 12: Format of the emissions report
Article 13: Scope of verification activities and verification report
In particular the verifier shall assess whether the CO 2 emissions and other relevant information included in the emissions report have been determined in accordance with Articles 8, 9 12 ='articles' class='internal-link article' href='#art_8' data-bs-toggle='popover' data-bs-trigger='hover focus' data-bs-content='Monitoring of activities within a reporting period' data-bs-placement='top' >8, 9 and 10 and the monitoring plan. 2
Article 14: General obligations and principles for the verifiers
Article 15: Verification procedures
Article 16: Accreditation of verifiers
Article 17: Document of compliance
Article 18: Obligation to carry a valid document of compliance on board
Article 19: Compliance with monitoring and reporting requirements and inspections
Article 20: Penalties, information exchange and expulsion order
Article 21: Publication of information and Commission report
Article 22: International cooperation
Article 23: Exercise of delegation
Article 24: Committee procedure
Article 25: Amendments to Directive 2009/16/EC
Article 26: Entry into force
Recital 1
Recital 2
Recital 3
Recital 4
Recital 5
Recital 6
Recital 7
Recital 8
Recital 9
Recital 10
Recital 11
Recital 12
Recital 13
Recital 14
Recital 15
Recital 16
Recital 17
Recital 18
Recital 19
Recital 20
Recital 21
Recital 22
Recital 23
Recital 24
Recital 25
Recital 26
Recital 27
Recital 28
Recital 29
Recital 30
Recital 31
Recital 32
Recital 33
Recital 34
Recital 35
Recital 36
Recital 37
Recital 38
Recital 39
Methods for monitoring CO 2 emissions Methods for monitoring CO 2 emissions
A. CALCULATION OF CO 2 EMISSIONS (ARTICLE 9) 2
For the purposes of calculating CO 2 emissions companies shall apply the following formula: 2
Fuel consumption × emission factor
Fuel consumption shall include fuel consumed by main engines, auxiliary engines, gas turbines, boilers and inert gas generators.
Fuel consumption within ports at berth shall be calculated separately.
In principle, default values for emission factors of fuels shall be used unless the company decides to use data on fuel quality set out in the Bunker Fuel Delivery Notes (BDN) and used for demonstrating compliance with applicable regulations of sulphur emissions.
Those default values for emission factors shall be based on the latest available values of the Intergovernmental Panel for Climate Change (IPCC). Those values can be derived from Annex VI to Commission Regulation 2012/601 ( 1 ) .
Appropriate emission factors shall be applied in respect of biofuels and alternative non-fossil fuels.
B. METHODS FOR DETERMINING CO 2 EMISSIONS 2
The company shall define in the monitoring plan which monitoring method is to be used to calculate fuel consumption for each ship under its responsibility and ensure that once the method has been chosen, it is consistently applied.
Actual fuel consumption for each voyage shall be used and be calculated using one of the following methods:
Method A: BDN and periodic stocktakes of fuel tanks
This method is based on the quantity and type of fuel as defined on the BDN combined with periodic stocktakes of fuel tanks based on tank readings. The fuel at the beginning of the period, plus deliveries, minus fuel available at the end of the period and de-bunkered fuel between the beginning of the period and the end of the period together constitute the fuel consumed over the period.
The period means the time between two port calls or time within a port. For the fuel used during a period, the fuel type and the sulphur content need to be specified.
This method shall not be used when BDN are not available on board ships, especially when cargo is used as a fuel, for example, liquefied natural gas (LNG) boil-off.
Under existing MARPOL Annex VI regulations, the BDN is mandatory, is to be retained on board for three years after the delivery of the bunker fuel and is to be readily available. The periodic stocktake of fuel tanks on-board is based on fuel tank readings. It uses tank tables relevant to each fuel tank to determine the volume at the time of the fuel tank reading. The uncertainty associated with the BDN shall be specified in the monitoring plan. Fuel tank readings shall be carried out by appropriate methods such as automated systems, soundings and dip tapes. The method for tank sounding and uncertainty associated shall be specified in the monitoring plan.
Where the amount of fuel uplift or the amount of fuel remaining in the tanks is determined in units of volume, expressed in litres, the company shall convert that amount from volume to mass by using actual density values. The company shall determine the actual density by using one of the following:
Method B: Bunker fuel tank monitoring on-board
This method is based on fuel tank readings for all fuel tanks on-board. The tank readings shall occur daily when the ship is at sea and each time the ship is bunkering or de-bunkering.
The cumulative variations of the fuel tank level between two readings constitute the fuel consumed over the period.
The period means the time between two port calls or time within a port. For the fuel used during a period, the fuel type and the sulphur content need to be specified.
Fuel tank readings shall be carried out by appropriate methods such as automated systems, soundings and dip tapes. The method for tank sounding and uncertainty associated shall be specified in the monitoring plan.
Where the amount of fuel uplift or the amount of fuel remaining in the tanks is determined in units of volume, expressed in litres, the company shall convert that amount from volume to mass by using actual density values. The company shall determine the actual density by using one of the following:
Method C: Flow meters for applicable combustion processes
This method is based on measured fuel flows on-board. The data from all flow meters linked to relevant CO 2 emission sources shall be combined to determine all fuel consumption for a specific period. 2
The period means the time between two port calls or time within a port. For the fuel used during a period, the fuel type and the sulphur content need to be monitored.
The calibration methods applied and the uncertainty associated with flow meters used shall be specified in the monitoring plan.
Where the amount of fuel consumed is determined in units of volume, expressed in litres, the company shall convert that amount from volume to mass by using actual density values. The company shall determine the actual density by using one of the following:
Method D: Direct CO 2 emissions measurement 2
The direct CO 2 emissions measurements may be used for voyages and for CO 2 emissions occurring in ports located in a Member State's jurisdiction. CO 2 emitted shall include CO 2 emitted by main engines, auxiliary engines, gas turbines, boilers and inert gas generators. For ships for which reporting is based on this method, the fuel consumption shall be calculated using the measured CO 2 emissions and the applicable emission factor of the relevant fuels. 2 2 2 2 2
This method is based on the determination of CO 2 emission flows in exhaust gas stacks (funnels) by multiplying the CO 2 concentration of the exhaust gas with the exhaust gas flow. 2 2
The calibration methods applied and the uncertainty associated with the devices used shall be specified in the monitoring plan.
( 1 ) Commission Regulation 2012/601 of 21 June 2012 on the monitoring and reporting of greenhouse gas emissions pursuant to Directive 2003/87 of the European Parliament and of the Council ( OJ L 181, 12.7.2012, p. 30 ).
Monitoring of other relevant information Monitoring of other relevant information
A. MONITORING ON A PER VOYAGE BASIS (ARTICLE 9)
For the purposes of monitoring other relevant information on an annual basis, companies shall respect the following rules:
The values to be monitored under Article 10 shall be determined by aggregation of the respective per voyage data.
Average energy efficiency shall be monitored by using at least four indicators: fuel consumption per distance, fuel consumption per transport work, CO 2 emissions per distance and CO 2 emissions per transport work, which shall be calculated as follows: 2 2
Elements to be taken into account for the delegated acts provided for in Articles 15 and 16 articles' class='internal-link article' href='#art_15' data-bs-toggle='popover' data-bs-trigger='hover focus' data-bs-content='Verification procedures' data-bs-placement='top' >15 and 16 Elements to be taken into account for the delegated acts provided for in Articles 15 and 16 articles' class='internal-link article' href='#art_15' data-bs-toggle='popover' data-bs-trigger='hover focus' data-bs-content='Verification procedures' data-bs-placement='top' >15 and 16
A. VERIFICATION PROCEDURES
Footnote p0: This Regulation shall be binding in its entirety and directly applicable in all Member States.
Done at Strasbourg, 29 April 2015.