This document is an excerpt from the EUR-Lex website
Document 02018R0841-20210314
Regulation (EU) 2018/841 of the European Parliament and of the Council of 30 May 2018 on the inclusion of greenhouse gas emissions and removals from land use, land use change and forestry in the 2030 climate and energy framework, and amending Regulation (EU) No 525/2013 and Decision No 529/2013/EU (Text with EEA relevance)Text with EEA relevance
Consolidated text: Regulation (EU) 2018/841 of the European Parliament and of the Council of 30 May 2018 on the inclusion of greenhouse gas emissions and removals from land use, land use change and forestry in the 2030 climate and energy framework, and amending Regulation (EU) No 525/2013 and Decision No 529/2013/EU (Text with EEA relevance)Text with EEA relevance
Regulation (EU) 2018/841 of the European Parliament and of the Council of 30 May 2018 on the inclusion of greenhouse gas emissions and removals from land use, land use change and forestry in the 2030 climate and energy framework, and amending Regulation (EU) No 525/2013 and Decision No 529/2013/EU (Text with EEA relevance)Text with EEA relevance
02018R0841 — EN — 14.03.2021 — 001.001
This text is meant purely as a documentation tool and has no legal effect. The Union's institutions do not assume any liability for its contents. The authentic versions of the relevant acts, including their preambles, are those published in the Official Journal of the European Union and available in EUR-Lex. Those official texts are directly accessible through the links embedded in this document
REGULATION (EU) 2018/841 OF THE EUROPEAN PARLIAMENT AND OF THE COUNCIL of 30 May 2018 on the inclusion of greenhouse gas emissions and removals from land use, land use change and forestry in the 2030 climate and energy framework, and amending Regulation (EU) No 525/2013 and Decision No 529/2013/EU (OJ L 156 19.6.2018, p. 1) |
Amended by:
|
|
Official Journal |
||
No |
page |
date |
||
COMMISSION DELEGATED REGULATION (EU) 2021/268 of 28 October 2020 |
L 60 |
21 |
22.2.2021 |
REGULATION (EU) 2018/841 OF THE EUROPEAN PARLIAMENT AND OF THE COUNCIL
of 30 May 2018
on the inclusion of greenhouse gas emissions and removals from land use, land use change and forestry in the 2030 climate and energy framework, and amending Regulation (EU) No 525/2013 and Decision No 529/2013/EU
(Text with EEA relevance)
Article 1
Subject matter
This Regulation sets out the commitments of Member States for the land use, land use change and forestry (‘LULUCF’) sector that contribute to achieving the objectives of the Paris Agreement and meeting the greenhouse gas emission reduction target of the Union for the period from 2021 to 2030. This Regulation also lays down the rules for the accounting of emissions and removals from LULUCF and for checking the compliance of Member States with those commitments.
Article 2
Scope
This Regulation applies to emissions and removals of the greenhouse gases listed in Section A of Annex I thereto, reported pursuant to Article 7 of Regulation (EU) No 525/2013 and that occur in any of the following land accounting categories on the territories of Member States:
During the periods from 2021 to 2025 and from 2026 to 2030:
(i) |
‘afforested land’ : land use reported as cropland, grassland, wetlands, settlements or other land, converted to forest land; |
(ii) |
‘deforested land’ : land use reported as forest land converted to cropland, grassland, wetlands, settlements or other land; |
(iii) |
‘managed cropland’ : land use reported as:
—
cropland remaining cropland,
—
grassland, wetland, settlement or other land, converted to cropland, or
—
cropland converted to wetland, settlement or other land;
|
(iv) |
‘managed grassland’ : land use reported as:
—
grassland remaining grassland,
—
cropland, wetland, settlement or other land, converted to grassland, or
—
grassland converted to wetland, settlement or other land;
|
(v) |
‘managed forest land’ : land use reported as forest land remaining forest land. |
As of 2026: ‘managed wetland’: land use reported as:
Article 3
Definitions
For the purposes of this Regulation, the following definitions apply:
‘sink’ means any process, activity or mechanism that removes a greenhouse gas, an aerosol, or a precursor to a greenhouse gas from the atmosphere;
‘source’ means any process, activity or mechanism that releases a greenhouse gas, an aerosol or a precursor to a greenhouse gas into the atmosphere;
‘carbon pool’ means the whole or part of a biogeochemical feature or system within the territory of a Member State and within which carbon, any precursor to a greenhouse gas containing carbon, or any greenhouse gas containing carbon is stored;
‘carbon stock’ means the mass of carbon stored in a carbon pool;
‘harvested wood product’ means any product of wood harvesting that has left a site where wood is harvested;
‘forest’ means an area of land defined by the minimum values for area size, tree crown cover or an equivalent stocking level, and potential tree height at maturity at the place of growth of the trees as specified for each Member State in Annex II. It includes areas with trees, including groups of growing, young, natural trees, or plantations that have yet to reach the minimum values for tree crown cover or an equivalent stocking level or minimum tree height as specified in Annex II, including any area that normally forms part of the forest area but on which there are temporarily no trees as a result of human intervention, such as harvesting, or as a result of natural causes, but which area can be expected to revert to forest;
‘forest reference level’ means an estimate, expressed in tonnes of CO2 equivalent per year, of the average annual net emissions or removals resulting from managed forest land within the territory of a Member State in the periods from 2021 to 2025 and from 2026 to 2030, based on the criteria set out in this Regulation;
‘half-life value’ means the number of years it takes for the quantity of carbon stored in a category of harvested wood products to decrease to one half of its initial value;
‘natural disturbances’ mean any non-anthropogenic events or circumstances that cause significant emissions in forests and the occurrence of which is beyond the control of the relevant Member State, and the effects of which the Member State is objectively unable to significantly limit, even after their occurrence, on emissions;
‘instantaneous oxidation’ means an accounting method that assumes that the release into the atmosphere of the entire quantity of carbon stored in harvested wood products occurs at the time of harvest.
Article 4
Commitments
For the periods from 2021 to 2025 and from 2026 to 2030, taking into account the flexibilities provided for in Articles 12 and 13, each Member State shall ensure that emissions do not exceed removals, calculated as the sum of total emissions and total removals on its territory in all of the land accounting categories referred to in Article 2 combined, as accounted in accordance with this Regulation.
Article 5
General accounting rules
Article 6
Accounting for afforested land and deforested land
Article 7
Accounting for managed cropland, managed grassland and managed wetland
During the period from 2021 to 2025, Member States that, pursuant to Article 2(2), have chosen not to include managed wetland in the scope of their commitments shall nevertheless report to the Commission on the emissions and removals from land use reported as:
wetland remaining wetland;
settlement or other land, converted to wetland; or
wetland converted to settlement or other land.
Article 8
Accounting for managed forest land
Forest reference levels as determined in accordance with the first subparagraph shall take account of the future impact of dynamic age-related forest characteristics in order not to unduly constrain forest management intensity as a core element of sustainable forest management practice, with the aim of maintaining or strengthening long-term carbon sinks.
Member States shall demonstrate consistency between the methods and data used to determine the proposed forest reference level in the national forestry accounting plan and those used in the reporting for managed forest land.
The Commission shall, where necessary, issue technical recommendations to the Member States reflecting the conclusions of the technical assessment to facilitate the technical revision of the proposed forest reference levels. The Commission shall publish those technical recommendations.
Article 9
Accounting for harvested wood products
In the accounts provided pursuant to Articles 6(1) and 8(1) relating to harvested wood products, Member States shall reflect emissions and removals resulting from changes in the carbon pool of harvested wood products falling within the following categories using the first order decay function, the methodologies and the default half-life values specified in Annex V:
paper;
wood panels;
sawn wood.
Article 10
Accounting for natural disturbances
Where a Member State applies paragraph 1, it shall:
submit to the Commission information on the background level for the land accounting categories referred to in paragraph 1 and on the data and methodologies used in accordance with Annex VI; and
exclude from accounting until 2030 all subsequent removals on the land affected by natural disturbances.
Article 11
Flexibilities
A Member State may use:
the general flexibilities set out in Article 12; and
in order to comply with the commitment in Article 4, the managed forest land flexibility set out in Article 13.
Article 12
General flexibilities
Article 13
Managed forest land flexibility
Where the result of the calculation referred to in Article 8(1) is a positive figure, the Member State concerned shall be entitled to compensate those emissions provided that:
the Member State, in its strategy submitted in accordance with Article 4 of Regulation (EU) No 525/2013, has included ongoing or planned specific measures to ensure the conservation or enhancement, as appropriate, of forest sinks and reservoirs; and
within the Union, total emissions do not exceed total removals in the land accounting categories referred to in Article 2 of this Regulation for the period for which the Member State intends to use the compensation. When assessing whether, within the Union, total emissions exceed total removals, the Commission shall ensure that double counting is avoided by Member States, in particular in the exercise of the flexibilities set out in this Regulation and Regulation (EU) 2018/842
As regards the amount of compensation, the Member State concerned may only compensate:
sinks accounted for as emissions against its forest reference level; and
up to the maximum amount of compensation for that Member State set out in Annex VII for the period from 2021 to 2030.
Article 14
Compliance check
Such report shall also contain, where applicable, details on the intention to use the flexibilities referred to in Article 11 and related amounts or on the use of such flexibilities and related amounts.
Article 15
Registry
Article 16
Exercise of delegation
Article 17
Review
On the basis of the findings of the report prepared pursuant to Article 14(3) and the results of the assessment carried out pursuant to point (b) of Article 13(2), the Commission shall, where appropriate, make proposals to ensure that the integrity of the Union’s overall 2030 greenhouse gas emission reduction target and its contribution to the goals of the Paris Agreement are respected.
Article 18
Amendments to Regulation (EU) No 525/2013
Regulation (EU) No 525/2013 is amended as follows:
In Article 7, paragraph 1 is amended as follows:
the following point is inserted:
as of 2023, their emissions and removals covered by Article 2 of Regulation (EU) 2018/841 of the European Parliament and of the Council ( *1 ) in accordance with the methodologies specified in Annex IIIa to this Regulation;
the following subparagraph is added:
‘A Member State may request to be granted a derogation by the Commission from point (da) of the first subparagraph to apply a different methodology from that specified in Annex IIIa where the methodology improvement required cannot be achieved in time for the improvement to be taken into account in the greenhouse gas inventories for the period from 2021 to 2030, or where the cost of the methodology improvement would be disproportionately high compared to the benefits of applying such methodology to improve accounting for emissions and removals due to the low significance of the emissions and removals from the carbon pools concerned. Member States wishing to benefit from this derogation shall submit a reasoned request to the Commission by 31 December 2020, indicating by which time the methodology improvement could be implemented, the alternative methodology proposed or both, and an assessment of the potential impacts on the accuracy of accounting. The Commission may request additional information to be submitted within a specific, reasonable time period. Where the Commission considers that the request is justified, it shall grant the derogation. If the Commission rejects the request, it shall give reasons for its decision.’.
In point (c) of Article 13(1), the following point is added:
as of 2023, information on national policies and measures implemented to meet their obligations under Regulation (EU) 2018/841 and information on additional national policies and measures planned with a view to limiting greenhouse gas emissions or enhancing sinks beyond their commitments under that Regulation;’.
In Article 14(1), the following point is inserted:
as of 2023, total greenhouse gas projections and separate estimates for the projected greenhouse gas emissions and removals covered by Regulation (EU) 2018/841’.
The following Annex is inserted:
Article 19
Amendment to Decision No 529/2013/EU
Decision No 529/2013/EU is amended as follows:
in Article 3(2), the first subparagraph is deleted;
in Article 6, paragraph 4 is deleted.
Article 20
Entry into force
This Regulation shall enter into force on the twentieth day following that of its publication in the Official Journal of the European Union.
This Regulation shall be binding in its entirety and directly applicable in all Member States.
ANNEX I
GREENHOUSE GASES AND CARBON POOLS
Greenhouse gases as referred to in Article 2:
carbon dioxide (CO2);
methane (CH4);
nitrous oxide (N2O).
Those greenhouse gases shall be expressed in terms of tonnes of CO2 equivalent and determined pursuant to Regulation (EU) No 525/2013.
Carbon pools as referred to in Article 5(4):
above-ground biomass;
below-ground biomass;
litter;
dead wood;
soil organic carbon;
harvested wood products in the land accounting categories of afforested land and managed forest land.
ANNEX II
MINIMUM VALUES FOR AREA SIZE, TREE CROWN COVER AND TREE HEIGHT PARAMETERS
Member State |
Area (ha) |
Tree crown cover (%) |
Tree height (m) |
Belgium |
0,5 |
20 |
5 |
Bulgaria |
0,1 |
10 |
5 |
Czech Republic |
0,05 |
30 |
2 |
Denmark |
0,5 |
10 |
5 |
Germany |
0,1 |
10 |
5 |
Estonia |
0,5 |
30 |
2 |
Ireland |
0,1 |
20 |
5 |
Greece |
0,3 |
25 |
2 |
Spain |
1,0 |
20 |
3 |
France |
0,5 |
10 |
5 |
Croatia |
0,1 |
10 |
2 |
Italy |
0,5 |
10 |
5 |
Cyprus |
0,3 |
10 |
5 |
Latvia |
0,1 |
20 |
5 |
Lithuania |
0,1 |
30 |
5 |
Luxembourg |
0,5 |
10 |
5 |
Hungary |
0,5 |
30 |
5 |
Malta |
1,0 |
30 |
5 |
Netherlands |
0,5 |
20 |
5 |
Austria |
0,05 |
30 |
2 |
Poland |
0,1 |
10 |
2 |
Portugal |
1,0 |
10 |
5 |
Romania |
0,25 |
10 |
5 |
Slovenia |
0,25 |
30 |
2 |
Slovakia |
0,3 |
20 |
5 |
Finland |
0,5 |
10 |
5 |
Sweden |
0,5 |
10 |
5 |
United Kingdom |
0,1 |
20 |
2 |
ANNEX III
BASE YEAR OR PERIOD FOR THE PURPOSE OF CALCULATING THE CAP PURSUANT TO ARTICLE 8(2)
Member State |
Base Year/Period |
Belgium |
1990 |
Bulgaria |
1988 |
Czech Republic |
1990 |
Denmark |
1990 |
Germany |
1990 |
Estonia |
1990 |
Ireland |
1990 |
Greece |
1990 |
Spain |
1990 |
France |
1990 |
Croatia |
1990 |
Italy |
1990 |
Cyprus |
1990 |
Latvia |
1990 |
Lithuania |
1990 |
Luxembourg |
1990 |
Hungary |
1985-87 |
Malta |
1990 |
Netherlands |
1990 |
Austria |
1990 |
Poland |
1988 |
Portugal |
1990 |
Romania |
1989 |
Slovenia |
1986 |
Slovakia |
1990 |
Finland |
1990 |
Sweden |
1990 |
United Kingdom |
1990 |
ANNEX IV
NATIONAL FORESTRY ACCOUNTING PLAN CONTAINING A MEMBER STATE’S FOREST REFERENCE LEVEL
A. Criteria and guidance for determining forest reference level
A Member State’s forest reference level shall be determined in accordance with the following criteria:
the reference level shall be consistent with the goal of achieving a balance between anthropogenic emissions by sources and removals by sinks of greenhouse gases in the second half of this century, including enhancing the potential removals by ageing forest stocks that may otherwise show progressively declining sinks;
the reference level shall ensure that the mere presence of carbon stocks is excluded from accounting;
the reference level should ensure a robust and credible accounting system that ensures that emissions and removals resulting from biomass use are properly accounted for;
the reference level shall include the carbon pool of harvested wood products, thereby providing a comparison between assuming instantaneous oxidation and applying the first-order decay function and half-life values;
a constant ratio between solid and energy use of forest biomass as documented in the period from 2000 to 2009 shall be assumed;
the reference level should be consistent with the objective of contributing to the conservation of biodiversity and the sustainable use of natural resources, as set out in the EU forest strategy, Member States’ national forest policies, and the EU biodiversity strategy;
the reference level shall be consistent with the national projections of anthropogenic greenhouse gas emissions by sources and removals by sinks reported under Regulation (EU) No 525/2013;
the reference level shall be consistent with greenhouse gas inventories and relevant historical data and shall be based on transparent, complete, consistent, comparable and accurate information. In particular, the model used to construct the reference level shall be able to reproduce historical data from the National Greenhouse Gas Inventory.
B. Elements of the national forestry accounting plan
The national forestry accounting plan submitted pursuant to Article 8 shall contain the following elements:
a general description of the determination of the forest reference level and a description of how the criteria in this Regulation were taken into account;
identification of the carbon pools and greenhouse gases which have been included in the forest reference level, reasons for omitting a carbon pool from the forest reference level determination, and demonstration of the consistency between the carbon pools included in the forest reference level;
a description of approaches, methods and models, including quantitative information, used in the determination of the forest reference level, consistent with the most recently submitted national inventory report, and a description of documentary information on sustainable forest management practices and intensity as well as of adopted national policies;
information on how harvesting rates are expected to develop under different policy scenarios;
a description of how each of the following elements were considered in the determination of the forest reference level:
the area under forest management;
emissions and removals from forests and harvested wood products as shown in greenhouse gas inventories and relevant historical data;
forest characteristics, including dynamic age-related forest characteristics, increments, rotation length and other information on forest management activities under ‘business as usual’;
historical and future harvesting rates disaggregated between energy and non-energy uses.
C. The forest reference levels to be applied by the Member States for the period from 2021 to 2025
Member State |
The forest reference level for the period from 2021 to 2025 in tonnes of CO2 equivalent per year |
Belgium |
– 1 369 009 |
Bulgaria |
– 5 105 986 |
Czech Republic |
– 6 137 189 |
Denmark |
+ 354 000 |
Germany |
– 34 366 906 |
Estonia |
– 1 750 000 |
Ireland |
+ 112 670 |
Greece |
– 2 337 640 |
Spain |
– 32 833 000 |
France |
– 55 399 290 |
Croatia |
– 4 368 000 |
Italy |
– 19 656 100 |
Cyprus |
– 155 779 |
Latvia |
– 1 709 000 |
Lithuania |
– 5 164 640 |
Luxembourg |
– 426 000 |
Hungary |
– 48 000 |
Malta |
– 38 |
Netherlands |
– 1 531 397 |
Austria |
– 4 533 000 |
Poland |
– 28 400 000 |
Portugal |
– 11 165 000 |
Romania |
– 24 068 200 |
Slovenia |
– 3 270 200 |
Slovakia |
– 4 827 630 |
Finland |
– 29 386 695 |
Sweden |
– 38 721 000 |
United Kingdom |
– 20 701 550 |
ANNEX V
FIRST ORDER DECAY FUNCTION, METHODOLOGIES AND DEFAULT HALF-LIFE VALUES FOR HARVESTED WOOD PRODUCTS
Methodological issues
Member States may use country-specific methodologies and half-life values instead of the methodologies and default half-life values specified in this Annex, provided that such methodologies and values are determined on the basis of transparent and verifiable data and that the methodologies used are at least as detailed and accurate as those specified in this Annex.
Default half-life values:
Half-life value means the number of years it takes for the quantity of carbon stored in a harvested wood products category to decrease to one half of its initial value.
Default half-life values shall be as follows:
2 years for paper;
25 years for wood panels;
35 years for sawn wood.
Member States may specify the wood-based material products, including bark, which fall within the categories referred to in points (a), (b) and (c) above, based on IPCC Guidelines as adopted by the Conference of the Parties to the UNFCCC or the Conference of the Parties serving as the Meeting of the Parties to the Paris Agreement, provided that the available data are transparent and verifiable. Member States may also use country-specific sub-categories of any of those categories.
ANNEX VI
CALCULATION OF BACKGROUND LEVELS FOR NATURAL DISTURBANCES
For the calculation of the background level, the following information shall be provided:
historical levels of emissions caused by natural disturbances;
the type(s) of natural disturbance included in the estimation;
total annual emissions estimations for those natural disturbance types for the period from 2001 to 2020, listed by land accounting categories;
a demonstration of the time series consistency in all relevant parameters, including minimum area, emission estimation methodologies, coverages of carbon pools and gases.
The background level is calculated as the average of the 2001-2020 time series excluding all years for which abnormal levels of emissions were recorded, i.e. excluding all statistical outliers. The identification of statistical outliers shall be undertaken as follows:
calculate the arithmetic average value and the standard deviation of the full time series 2001-2020;
exclude from the time series all years for which the annual emissions are outside twice the standard deviation around the average;
calculate again the arithmetic average value and the standard deviation of the time series 2001-2020 minus the years excluded in point (b);
repeat points (b) and (c) until no outliers can be identified.
After calculating the background level pursuant to point 2 of this Annex, if emissions in a particular year in the periods from 2021 to 2025 and from 2026 to 2030 exceed the background level plus a margin, the amount of emissions exceeding the background level may be excluded in accordance with Article 10. The margin shall be equal to a probability level of 95 %.
The following emissions shall not be excluded:
emissions resulting from harvesting and salvage logging activities that took place on land following the occurrence of natural disturbances;
emissions resulting from prescribed burning that took place on land in any year of the period from 2021 to 2025 or from 2026 to 2030;
emissions on lands that were subject to deforestation following the occurrence of natural disturbances.
Information requirements pursuant to Article 10(2) include the following:
identification of all land areas affected by natural disturbances in that particular year, including their geographical location, the period and types of natural disturbances;
evidence that no deforestation has occurred during the rest of the period from 2021 to 2025 or from 2026 to 2030 on lands that were affected by natural disturbances and in respect of which emissions were excluded from accounting;
a description of verifiable methods and criteria to be used to identify deforestation on those lands in the subsequent years of the period from 2021 to 2025 or from 2026 to 2030;
where feasible, a description of measures the Member State undertook to prevent or limit the impact of those natural disturbances;
where feasible, a description of measures the Member State undertook to rehabilitate the lands affected by those natural disturbances.
ANNEX VII
MAXIMUM AMOUNT OF COMPENSATION AVAILABLE UNDER THE MANAGED FOREST LAND FLEXIBILITY REFERRED TO IN POINT (B) OF ARTICLE 13(3)
Member State |
Reported average removals by sinks from forest land for the period from 2000 to 2009 in million tonnes of CO2 equivalent per year |
Compensation limit expressed in million tonnes of CO2 equivalent for the period from 2021 to 2030 |
Belgium |
-3,61 |
-2,2 |
Bulgaria |
-9,31 |
-5,6 |
Czech Republic |
-5,14 |
-3,1 |
Denmark |
0,56 |
0,1 |
Germany |
-45,94 |
-27,6 |
Estonia |
-3,07 |
-9,8 |
Ireland |
0,85 |
0,2 |
Greece |
-1,75 |
-1,0 |
Spain |
-26,51 |
-15,9 |
France |
-51,23 |
-61,5 |
Croatia |
-8,04 |
-9,6 |
Italy |
-24,17 |
-14,5 |
Cyprus |
0,15 |
0,03 |
Latvia |
-8,01 |
-25,6 |
Lithuania |
-5,71 |
-3,4 |
Luxembourg |
0,49 |
0,3 |
Hungary |
-1,58 |
0,9 |
Malta |
0,00 |
0,0 |
Netherlands |
-1,72 |
0,3 |
Austria |
-5,34 |
-17,1 |
Poland |
-37,50 |
-22,5 |
Portugal |
-5,13 |
-6,2 |
Romania |
-22,34 |
-13,4 |
Slovenia |
-5,38 |
-17,2 |
Slovakia |
-5,42 |
-6,5 |
Finland |
-36,79 |
-44,1 |
Sweden |
-39,55 |
-47,5 |
United Kingdom |
-16,37 |
-3,3 |
( *1 ) Regulation (EU) 2018/841 of the European Parliament and of the Council of 30 May 2018 on the inclusion of greenhouse gas emissions and removals from land use, land use change and forestry in the 2030 climate and energy framework and amending Regulation (EU) No 525/2013 and Decision No 529/2013/EU (OJ L 156, 19.6.2018, p. 1).’;