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REPORT
Methane Emissions
in a Danish Context
Mapping of Denmark's current and projected methane
emissions and how we can reduce them
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GREEN TRANSITION DENMARK
Green Transition Denmark
is an independent environmental organization that works to
promote a green and sustainable transformation of society.
The Methane Matters Coalition
consists of experienced non-governmental organisations
working to significantly reduce methane emissions in the relevant agriculture, waste and
energy sectors by 2030. Green Transition Denmark is a partner organisation of the Coalition.
This report is funded by the Methane Matters Coalition
Published:
December 2024
Authors:
Lærke Kjærbye-Thygesen (Policy Officer at Green Transition Denmark), Christian
Ege (Senior Consultant at Green Transition Denmark), and Niklas Sjøbeck Jørgensen (Senior
Policy Officer at Green Transition Denmark).
Acknowledgements:
Thanks to our colleagues for their input and feedback: Erik Tang (Green
Transition Denmark), Trine Langhede (Green Transition Denmark), and Julie Bangsgaard
Abrahams (Green Transition Denmark).
Green Transition Denmark / Rådet for Grøn Omstilling
Kompagnistræde 22, 3
1208 København K
Danmark
[email protected]
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RECOMMENDATIONS
1.
The Danish Government must develop a National Methane Action Plan with a
reduction target of 40-45%.
2. The short-term perspective (GWP20) should be incorporated in the decision-
making as the deadline of most climate goals are within the next 20-25 years.
3. Danish agriculture should be transformed resulting in less animal production and
more plant-based food production
4. The trade-offs in the use of mitigation technologies must be thoroughly explored
and taken into consideration before they are implemented.
5. Oil and fossil natural gas extraction must be phased out before 2040. This is
possible, according to our recent energy transition scenario.
6. The target of phasing-out the use of oil and gas boilers must be advanced to
2030.
7. Methane leakage from biogas plants must be closely monitored and addressed,
including the real impact of the new regulation on methane leakage.
8. The production and use of biogas must be in accordance with a significant
reduction in livestock numbers and feedstock for plants should primarily be
based on residues.
9. Biogas should only be used where there are no better alternatives – e.g. in peak
load production (supplementary to wind and solar power) and in industries
requiring high temperatures.
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Table of Contents
Danish Summary…………………………………………………………………………………………………………………..…4
Executive Summary………………………………………………………………………………………………………………….5
The Global Methane Pledge (GMP)..………………………………………………………………………………………....6
Why Is Methane Important?…………………………………………………………………………………………………..…7
Global Warming Potential………………………………………………………………………………………………………………………….7
Sources of Methane Emissions
……………………………………………………………………………………………………..…...9
National Methane Action Plans……………………………………………………………………………………………….10
How to Develop a Danish Methane Action Plan…………………………………………………………………………………………11
Sources of Methane Emissions in Denmark…………………………………………………………………………….12
Projection of Danish Methane Emissions………………………………………………………………………………………………….13
Agriculture Sector…………………………………………………………………………………………………………..………15
Enteric Fermentation………………………………………………………………………………………………………………………...…….16
Feed additives and optimization are not enough……………………………………………………………………………………………….…….17
Manure Management………………………………………………………………………………………………………………………………18
Waste Sector………………………………………………………………………………………………………………..………..19
Anaerobic Digestions at Biogas Plants……………………………………………………………………………………..………………19
Solid Waste Disposal………………………………………………………………………………………………………………..……………..20
Energy Sector…………………………………………………………………………………………………………………….…..21
Energy Industries and Other Sectors…………………………………………………………………………………………….………….21
Gas in the heating sector should be phased out……………………………………………………………………………………..…………….…22
Fugitive Emissions…………………………………………………………………………………………………………………………….…….22
Land Use, Land Use Change and Forestry (LULUCF)………………………………………………………………..23
Conclusions……………………………………………………………………………………………………………………………24
Green Transition Denmark’s 9 Recommendations Elaborated…………………………………………………25
References………………………………………………………………………………………………………….…………………27
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Danish Summary
Metan er en kortlivet, men kraftig drivhusgas, der er årsag
til cirka en tredjedel af den totale globale opvarmning, vi
oplever i dag. Metan opvarmer planeten omkring 30
gange mere end CO2 beregnet over en 100-årig periode,
men over 80 gange mere over en 20-årig periode. Jo mere
bekymrede vi er for global opvarmning på den korte bane,
jo mere bør vi derfor fokusere på at reducere metan-
udledninger. Med de fleste klimamål inden for de næste
20-25 år, og en snarlig overskridelse af 1.5°C-målet og
flere ’tipping points’, kan reduktioner af metan-udledning
til atmosfæren skabe hurtige og markante effekter på
opvarmningen og købe tid til mere langsigtede CO2-
reduktionsstrategier.
I 2021 lancerede EU sammen med USA the Global
Methane Pledge (GMP) på COP26, hvis primære mål er at
reducere de globale metan-udledninger med 30% i 2030
i forhold til 2020. I marts 2024 havde 158 lande skrevet
under på GMP, deriblandt Danmark. Fremskrivninger fra
Klima, Energi og Forsyningsministeriet viser dog, at
Danmark kun ser ud til at reducere deres metan-
udledninger med 10-15%. De danske metan-udledninger
kommer fra henholdsvis landbrugs-, affalds-, energi- og
LULUCF-sektoren, hvor landbruget står for klart den
største andel af udledningerne.
Effekterne af den grønne trepart er ikke medtaget, da
effekterne heraf endnu er usikre. Tilskuddet til
fodertilsætningsstoffet Bovaer vurderes at bidrage til en
metanreduktion på op til fem procentpoint i 2030 i forhold
til 2020, mens det er usikkert, hvor meget antallet af
husdyr vil blive reduceret som følge af aftalen og dermed,
hvad den tilhørende metanreduktion vil være. Derudover
vil aftalen øge metanudledningen fra lavbundsjorder, men
den samlede klimaeffekt af vådlægningen vil dog være
positiv. Rådet for Grøn Omstilling forventer ikke, at
effekterne
af
trepartsaftalen
vil
reducere
metanudledningen tilstrækkeligt og er fortsat skeptiske
over for potentielle negative sideeffekter af Bovaer.
Rådet for Grøn Omstilling anbefaler, at den danske
regering udvikler en national metan-handlingsplan med et
reduktionsmål på 40-45 %. Dette reduktionsmål er
nødvendigt for at sikre overensstemmelse med Paris-
aftalen og the Global Methane Pledge, og er vurderet
omkostningseffektivt
og
gennemførligt
af
FN’s
miljøprogram. Fokus skal være på at transformere
landbruget mod mere plantebaseret produktion for at
reducere metan-udledningerne fra sektoren, der i dag står
for 80% af udledningerne. Dette kan kun lade sig gøre ved
en kombination af strukturel og teknologisk omstilling.
Det skal samtidig sikres, at teknologiske virkemidler ikke
har negative sideeffekter, f.eks. på dyrevelfærd og
biodiversitet.
De største kilder til metan-udledninger i Danmark er
husdyrenes fordøjelsesprocesser og husdyrgødning i
landbrugssektoren,
deponering
af
vådområder
affald
og
i
LULUCF-sektoren,
metan-lækage
fra
fast
biogasanlæg i affaldssektoren, samt flygtige emissioner
fra gas i energisektoren. For at leve op til hvad Danmark
skrev under på i the Global Methane Pledge, skal
Danmark udforme en national metan-handlingsplan, der
viser hvordan Danmark vil reducere sine metan-
udledninger med mindst 30% i 2030 i forhold til 2020.
Metan-udledninger fra energisektoren bør reduceres ved
at udfase olie- og naturgasudvinding inden 2040.
Installation af nye olie- og gasfyr bør straks forbydes, og
de eksisterende bør udfases senest i 2030.
Desuden skal metan-lækage fra biogasanlæg overvåges,
grænseværdierne skal gradvist skærpes, og de skal
håndhæves. Biogasproduktionens størrelse skal kunne
kombineres med en betydelig reduktion i antallet af
husdyr. Biogas skal kun bruges, hvor der ikke er bedre
alternativer, f.eks. som supplement til vind og sol, samt til
forsyning af industrier med særlige behov.
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Executive Summary
Methane is a short-lived but powerful greenhouse gas that
is responsible for about a third of the total net global
warming we are experiencing today. Methane warms the
planet about 30 times more than CO2 calculated over a
100-year period, but over 80 times more over a 20-year
period. Therefore, the more concerned we are about
global warming in the short term, the more emphasis we
must put on cutting methane emissions. With most
climate targets due to be met within the next 20-25 years,
and the threat of soon exceeding the 1.5°C target and
multiple ‘tipping points’, reducing methane emissions can
have a rapid and significant impact on global warming and
buy time for longer-term CO2 mitigation strategies.
In 2021, the EU and the US launched the Global Methane
Pledge (GMP) at COP26. The main goal of the GMP is to
reduce global methane emissions by 30% in 2030
compared to 2020. By March 2024, 158 countries had
signed the GMP, including Denmark. However, projections
from the Danish Ministry of Climate, Energy and Utilities
show that Denmark will only be reducing its methane
emissions by 10-15%. Danish methane emissions come
from the agriculture, waste, energy and LULUCF sectors,
with agriculture accounting for by far the largest share of
emissions.
The effects of the Danish political agreement - the Green
Tripartite Agreement - are not included as the effects are
still uncertain. The subsidy for the feed additive Bovaer is
estimated to contribute to a methane reduction of up to
five percentage points in 2030 compared to 2020, while
it is uncertain how much livestock numbers will be
reduced as a result of the agreement, and thus what the
associated methane reductions will be. In addition, the
agreement will increase methane emissions from
peatlands, but the overall climate effect of rewetting will
be positive. Green Transition Denmark does not expect
the effects of the tripartite agreement to sufficiently
reduce methane emissions and remains skeptical about
possible negative side effects of Bovaer.
5
Methane emissions from the energy sector should be
reduced by phasing out oil and natural gas extraction by
2040. The installation of new oil and gas boilers should
be banned immediately, and existing boilers should be
phased out by 2030 at the latest. In addition, methane
leakage from biogas plants must be monitored and limits
gradually tightened and enforced. The scale of biogas
production must be compatible with a significant
reduction in livestock numbers. Biogas should only be
used where there are no better alternatives, e.g. to
supplement wind and solar power, and to supply
industries with special needs.
Green Transition Denmark recommends that the Danish
government develops a National Methane Action Plan
with a reduction target of 40-45%. This reduction target is
necessary to ensure compliance with the Paris Agreement
and the Global Methane Pledge and has been deemed
cost-effective and feasible by the UN Environment
Programme (UNEP). The focus should be on transforming
agriculture towards more plant-based production to
reduce methane emissions from the sector, which
currently accounts for 80% of Danish methane emissions.
This can only be achieved through a combination of
structural and technological transformation. At the same
time, it must be ensured that technological measures do
not have negative side effects, for example on animal
welfare and biodiversity.
The largest sources of methane emissions in Denmark are
enteric fermentation and manure management in the
agriculture sector, wetlands in the LULUCF sector, solid
waste disposal and methane leakage from biogas plants
in the waste sector, and fugitive emissions from gas in the
energy sector. In order to fulfil Denmark's commitment to
the Global Methane Pledge, Denmark must develop a
National Methane Action Plan showing how Denmark will
reduce its methane emissions by at least 30% in 2030
compared to 2020.
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The Global Methane Pledge (GMP)
In 2021 the EU and the United States together launched
the Global Methane Pledge (GMP) at COP26 in Glasgow to
accelerate action to reduce methane emissions. The main
goal of the Pledge is to reduce global methane emissions
by 30% in 2030 compared to 2020 levels. The reduction
target is global rather than national, meaning that each
participant of the GMP has agreed to
take voluntary
actions to contribute to a collective effort to reduce global
methane emissions by at least
30%
2
. The pledge
emphasises the importance of rapidly reducing methane
emissions to limit global warming to 1.5°C, in line with the
Paris Agreement.
In March 2024 the GMP counted 158 participants, who
together
account
for
just
over
50%
of
global
anthropogenic methane emissions.
The
participants
have
committed
to
taking
comprehensive national actions to achieve the reduction
target by
focusing on standards to achieve all feasible
reductions in the energy and waste sectors and seeking
abatement of agricultural emissions through technology
innovation as well as incentives and partnerships with
farmers
3
. Denmark, led by the former climate and energy
minister Dan Jørgensen, signed the GMP at its launch in
2021, and is thereby one of the 158 countries that has
committed to collectively reduce the global methane
emissions with 30 % and to take comprehensive domestic
actions to achieve that target. As not all countries in the
world have signed the GMP, calculations by the UK think
tank Green Alliance show that all GMP participants must
reduce their methane emissions by more than 40% to
ensure that the GMP's 30% reduction target is met
4
.
Figure 1: Participants of the GMP (in blue)
5
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Why is Methane Important?
Methane
(CH4)
is
the
second
most
important
Figure 2: The Danish projected greenhouse gas
emissions in 2030 based on GWP100 and GWP20
10
25
anthropogenic greenhouse gas (GHG) in terms of its
warming effect
6
. According to the sixth assessment report
from the Intergovernmental Panel on Climate Change
(IPCC), about a third of the total net global warming since
pre-industrial
levels
is
due
to
higher
methane
20
GWP100
concentrations
7
. Methane warms the planet about 30
times more than CO2 calculated over a 100-year period,
but over 80 times more over a 20-year
period
8
.
This
means that the global warming potential (GWP) of
methane is about three times higher in the short term (20
years) than in the long term (100 years).
The GWP describes the total warming effect caused by the
instantaneous emission over the entire period (in this
case over 20 or 100 years), i.e. 1 tonne of methane over
100 years has a warming effect equivalent to 28 tonnes
of CO2, while 1 tonne of methane over 20 years has a
warming effect equivalent to 84 tonnes of CO2
9
. The
difference in the GWP of methane is due to the short
lifetime of methane in the atmosphere of 12-15 years.
The high GWP of methane compared to carbon dioxide in
the short term makes methane reductions an attractive
target for rapidly mitigating global warming in the near
term.
This is reflected in Figure 2, which shows the projections
of Danish greenhouse gases in 2030, calculated in CO2
equivalents based on the GWP of the gases over 20 and
100 years. In the short term, methane emissions account
for a much higher proportion of the global warming effect
of greenhouse gas emissions, which is why methane
reductions are much more important in this perspective
than reductions in carbon dioxide or nitrous oxide. In other
words, the more concerned we are about short-term
global warming, the more emphasis we must put on
cutting methane emissions.
The 100-year perspective also misses the threat of
‘tipping points’ that will result in irreversible changes and
damage the planet’s life-support systems when crossed
12
.
With the current warming level five major tipping points
are at risk of being crossed, and if the 1.5°C global
warming is exceeded three more tipping points are at risk
of being crossed (see the box below). The short lifetime of
7
5
mio. ton CO2e
15
GWP20
10
0
Co2
CH4
N20
SF6
Global Warming Potential
Currently,
effects
of
most
climate-models
gases,
use
this
a
100-year
the
perspective in their judgements of the temperature
greenhouse
includes
Intergovernmental Panel on Climate Change (IPCC)
11
. The
climate projections that compare the warming effect of
different greenhouse gases look 100 years ahead to
2100. But the situation has changed since the decision
was taken to focus on the 100-year perspective. With
greenhouse gas emissions remaining high, climate
change accelerating globally, and climate targets for
2030 and 2050 approaching, a 10–25-year time horizon
is much more relevant for assessing how to best mitigate
climate change. In this perspective, methane emissions
have a much larger impact on the overall temperature rise
in the near future.
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methane could be the key to avoiding the harmful tipping
points of climate change and buying time for longer-term
CO2 mitigation strategies. Therefore, the rapid effect, and
thus importance, of methane reductions must be
considered in policy decisions and actions.
Reducing methane emissions is not only an effective way
to rapidly reduce global warming, but also to improve
human and ecosystem health. Methane contributes to the
formation of ground-level ozone, and thus to air pollution,
which causes
significant impacts on human health and
vegetation, including agricultural crops, forests and other
plants, as it reduces their growth rates and yields and has
negative
services
13
.
Tipping Points
In addition, ozone air pollution causes about one million
premature deaths a year worldwide (about 24.000 in the
EU
14
), and economic losses due to reduced crop
productivity
15
. Reducing methane emissions therefore
contributes both to mitigating climate change and to
improving human and ecosystem health through better air
quality.
impacts
on
biodiversity
and
ecosystem
At today’s 1.2°C global warming five major tipping points are at risk of being crossed. If they are crossed, it will result in
irreversible changes and damage the planet’s life-support systems. These are warm-water coral reefs, the ice sheets of
Greenland and West Antarctica, the North Atlantic’s Subpolar Gyre circulation, and parts of the permafrost (see Figure 3).
If the 1.5°C global warming is exceeded three more potential tipping points become vulnerable: boreal forest, mangroves
and seagrass meadows.
Figure 3: Parts of the Earth system identified as tipping points by Global Tipping Points Report
16
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Sources of Methane Emissions
Global methane emissions come from both natural and
anthropogenic sources, i.e. emissions resulting from
human activities. Natural emissions account for around
40% of global methane emissions and come mainly from
wetlands
17
. The anaerobic soil conditions that are a
natural function of wetlands lead to the release of
methane, but at the same time wetlands also serve as
carbon sinks, regulate the water cycle and support 40% of
the world’s biodiversity
18
. Anthropogenic emissions
account for 60% of the emissions and the main sources
of these emissions are agriculture (animal husbandry and
land use), energy (extraction and transport of fossil fuels)
and waste (landfills and wastewater)
19
.
As shown in Figure 4, agriculture is the largest contributor
to methane emissions both globally and in the EU,
accounting for 40% and 54% of methane emissions
respectively. The energy sector is the second largest
emitter of methane globally, but the third largest in the EU.
One reason for this difference is that methane emissions
linked to fossil fuel imports are not included in the
inventory for EU presented in Figure 4. As shown in Figure
5, EU’s methane emissions from the energy sector would
be much higher if imported oil and gas were included.
Within the EU, methane emissions from the waste and
energy sectors have decreased since the 1990’s, while
the emissions from agriculture have remained more
stable.
Figure 4: Global and EU Emission Sources of Anthropogenic Methane
20
Global Emission Sources of Anthropological Methane
A
Other 5%
Waste 27%
Waste 20%
Agriculture
40%
EU Emission Sources of Anthropological Methane
B
Energy 19%*
Energy 35%
Agriculture
54%
*This does not include methane emissions linked to fossil fuel imports.
(The EU relies on imports for 70% of its coal consumption, 97% of its consumption and 90% of its fossil gas consumptions.)
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Figure 5: Development of EU’s methane emissions
21
300.000
*
250.000
200.000
kt CO2e
150.000
100.000
50.000
0
1996
1998
2000
Energy
2002
2004
2006
Agriculture
2008
2010
2012
Waste
2014
2016
2018
2020
2022
*
EU methane emissions from the energy sector when imported oil and gas are included
National Methane Action Plans
As part of the commitment to the Global Methane Pledge
(GMP), countries are expected to submit a Methane
Action Plan outlining existing policies and future activities
to reduce methane by 2030 and beyond. As of October
2023, nearly 60 governments and the European Union
have completed or are in the process of completing their
National Methane Action Plans
22
. Among the Nordic
countries, Denmark is the only country that has not
submitted a Methane Action Plan
23
. Among the countries
that have submitted their Methane Action Plan, the
expected methane reductions between 2020 and 2030
vary widely. For example, Iceland expects its methane
emissions to decrease by 1%, Sweden by 17%, the EU by
23%, and Canada by 35%, while projections show that
Denmark’s methane emissions will decrease between 10-
15% in 2030 compared to 2020
24
.
In its Methane Action Plan, the EU specifically mentions
One reason for the large variation in the expected
methane reductions across countries is the difference in
the size of the different sectors. The GMP states that the
energy sector has the greatest potential for targeted
reductions
by
2030
25
.
Methane
emissions
from
agriculture are, according to the GMP and its initiators,
the challenges of high costs and biological processes
associated with methane reductions in the agriculture
sector as a reason why the EU will not reduce its methane
emissions by 30% in 2030 compared to 2020. Methane
emissions in the energy and waste sectors will be reduced
by more than 30% over this period, but as most of the EU's
methane emissions come from the agriculture sector,
10
USA and the EU, more challenging to reduce due to high
costs and the nature of the biological processes involved.
Therefore, reductions will require technological innovation
as well as incentives and partnerships with farmers,
according to the EU
26
. Most proven technologies and
practices, particularly in the fossil fuel and waste sectors,
can be implemented at negative or low cost, making
methane reductions in these sectors more accessible
27
.
But abating methane emissions from agriculture can also
be addressed in a more systemic way by changing what
we produce. Since the vast majority of methane emissions
stem from animal husbandry, it would lead to substantial
reductions if we transformed our production systems
towards producing less animal products and more plant-
based food for human consumption.
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where emissions by the sector and the authorities are
regarded as harder to reduce, the EU will not meet the
30% reduction target
28
. If the EU makes systemic changes
to the agricultural production, greater reductions could be
achieved. The 30% reduction target could arguably be set
higher considering the effects of an agricultural
production system change.
The reduction target in the Danish Methane Action Plan
should be at least a 30% reduction (in line with the GMP)
by 2030, but preferably of a 40-45% reduction by 2030,
which is considered both cost-effective and feasible in the
Global Methane Assessment
29
. This target must be the
focal point of a Danish Methane Action Plan that sets out
the path with concrete and new policies that makes it
possible to achieve the reduction target.
How to develop a Danish Methane Action
Plan?
EU's Methane Action Plan, as well as those of the other
Nordic countries, is more or less structured around five
building blocks developed by the Climate and Clean Air
Coalition (CCAC). The five building blocks are listed in the
box below. Denmark can therefore easily use these
building blocks to develop a Danish Methane Action Plan.
In the Danish context, it is specifically urgent to address
methane from the agriculture sector and seek pathways
to reduce the sector’s emissions, e.g. by addressing the
size of livestock production, as the current level is far from
sustainable (this will be elaborated below). In order to lead
to real reductions in methane emissions, the plan must
both set specific sub-targets and outline concrete
measures.
The Five Building Blocks of a National Methane Action Plan Developed by CCAC
30
Building Block #1 - Emissions:
Quantification of national total methane emissions disaggregated by major
source sectors for recent historic years
Building Block #2 - Analytics:
Data, tools and methods to identify, evaluate and prioritise methane mitigation
measures
through quantitative assessment of the emission reduction and additional benefits achievable from
their implementation
Building Block #3 - Targets:
Communicated target that outlines a commitment that will achieve a reduction
in methane emissions
Building Block #4 - Implementation Pathways:
A concrete set of actions that provide a clear pathway to the
implementation of priority methane mitigation measures, accounting for different types of regulatory,
legislative, infrastructure, financing, incentive, monitoring and enforcement, communication and other actions
necessary for implementation. Also accounting for barriers to implementation and how these can be
overcome, as well as how these actions can be turned into fundable projects.
Building Block #5 - Monitoring, Reporting and Verification:
Systems in place to sustainably track progress on
i) implementation of priority measures, ii) actions needed for their implementation and iii) impacts from their
implementation.
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Sources of Methane Emissions in Denmark
Figure 6: Development in Danish methane emissions compared to Danish CO2 emissions
31
90
80
70
60
mio. ton CO2e
mio. ton CO2e
12
10
8
50
40
30
20
10
0
1990
1994
1998
CO2
2002
2006
2010
2014
2018
2022
6
4
2
0
1990
1994
1998
2002
2006
2010
2014
2018
2022
CH4 - (CO2 equivalent)
CH4 - (CO2 equivalent)
While total Danish CO2 emissions have decreased since
1990, Danish methane emissions have been much more
stable, with a small decrease since 1990 (see Figure 6).
The current Danish methane emissions come mainly from
agriculture, the waste sector, and the energy sector.
Denmark differs from both global and EU distribution of
emissions in how much agriculture contributes to the
national methane emissions. Agriculture accounts for
80% of methane emissions in Denmark (see Figure 7),
while it “only” accounts for 54% of methane emissions in
the EU
32
. Agriculture is therefore the main source of
methane emissions. Where the Danish methane
emissions from the energy sector and partly the waste
sector have decreased since 1990, methane emissions
from the agriculture sector have remained stable and high
(see Figure 8).
Figure 7: Danish Methane Emissions in 2023
33
(IPCC Sectors)
Waste 12%
LULUCF 4%
Energy 4%
Figure 8: Development of Danish Methane Emissions
34
(Sector Level)
8
7
6
mio. ton CO2e
5
4
3
2
1
0
1990 1993 1996 1999 2002 2005 2008 2011 2014 2017 2020 2023
Agriculture 80%
TOTAL Energy Sector
TOTAL Agriculture Sector
Enteric fermentation
Manure management
TOTAL LULUCF Sector
TOTAL Waste Sector
Anaerobic digestion at biogas facilities
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GREEN TRANSITION DENMARK
Projection of Danish Methane Emissions
Figure 9: Projection of Danish Methane Emissions from 2020-2035
35
(Mio. Ton Co2e based on GWP100)
10
9
8
7
6
5
4
3
2
1
0
2020
2021
2022
2023
2024
2025
Energy
2026
2027
2028
2029
2030
Waste
2031
2032
2033
2034
2035
Agriculture
LULUCF
The 2024 projections on the development of greenhouse
gas emissions, published annually by the Danish Ministry
of Climate, Energy and Utilities, show that Danish
methane emissions are expected to decrease in the
future
36
. The decrease in methane emissions is expected
to occur in the energy and agriculture sectors, while
methane emissions are expected to increase in the waste
and in the Land Use, Land Use Change and Forestry
(LULUCF) sectors. However, the increase in methane
emissions from the LULUCF-sector is due to an increase
in wetlands, as carbon-rich agricultural land is set-aside
and rewetted
37
. Despite the resulting increase in methane
emissions, rewetting of carbon-rich agricultural land has a
significant net positive effect on the climate of 10-40
tonnes of CO2 per hectare, as wetlands also serve as
carbon sinks
38
. Rewetting also entails positive effect on
the aquatic environment, as rewetting reduces nitrogen
leaching
39
.
Overall, Danish methane emissions are projected to
decrease by 10-15% in 2030 compared to 2020. Whether
the reduction will be 15% or 10% depends on whether a
regulation on methane leakage from biogas production is
included, as it is expected to decrease methane
emissions from biogas production. There is currently no
ex-post analysis of the effect of the regulation, which is
why it is not directly included in the projections of total
methane emissions. If the regulatory potential regarding
methane leakage is fully realized, the waste sector will
decrease its methane emissions by 16% in 2030
compared to 2020. Including this potential in the
projection thus changes the outcome significantly.
The effects of the new Danish political agreement - the
Green Tripartite Agreement - are not included in the
projections of methane emissions. Three important
effects of the Green Tripartite Agreement are worth
highlighting in relation to methane. First, the agreement
will lead to increased rewetting of carbon-rich peatlands,
which will lead to increased methane emissions. However,
the overall climate effect of rewetting will be positive.
Secondly, a subsidy for the feed additive Bovaer will be
introduced from 2025, resulting in an estimated methane
reduction from
feed
additives of
0.4
million
tonnes annually between 2025 and 2030
40
. Thereafter,
the marginal tax rate will exceed the cost of the feed
additive, which is why the effect of Bovaer is not estimated
13
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GREEN TRANSITION DENMARK
from 2030 onwards. When the estimated effect of Bovaer
is included in the total methane reduction calculations,
the use of feed additives could result in a reduction of up
to 5 percentage points. Thirdly, the agreement is expected
to lead to a reduction in livestock numbers (which will
have the largest impact on methane reductions in the
agricultural sector). How much livestock numbers will be
reduced and what the associated effect will be is highly
uncertain. In conclusion, Green Transition Denmark does
not expect the effects of the Tripartite agreement to
reduce methane emissions sufficiently and remain
skeptical of potential negative side-effects of Bovaer.
‘The Climate Status and Projection’ accounts for methane
emissions in CO2e based on the global warming potential
over 100 years (GWP100). If Danish methane emissions
were instead calculated in terms of their 20-year global
warming potential (GWP20), the climate impact would be
three times higher, and so would expected-reductions. A
30% reduction of methane emissions from 2020 to 2030
(in line with the GMP) measured based on GWP20, would
thereby result in a reduction of 8 million tons CO2e
41
. A
40-45% reduction, which is needed to honor the Paris
Agreement, would result in reductions of 10.7-12 million
tons CO2e.
Table 1: Projection of the Change in Danish Methane Emissions from 2020-2030
42
(Mio. Ton Co2e based on GWP100)
Sectors
2020
2030
% reduction from 2020 to 2030
*
Energy
Agriculture
LULUCF
Waste
0.37
7.28
0.3
0.96
0.25
5.96
0.51
1.34
**
-32 %
-18 %
70 %
40 %
***
Total
Total with partial correction regarding
methane leakage from biogas
production
8.91
8.06
-10 %
8.91
7.53
-15 %
* If the estimated effect of the feed additive Bovaer is included, the number for agriculture in 2030 is 5.56 and methane emissions would be
reduced by up to 5 percentage points. This results in a total reduction of 15-20%.
** If the correction regarding methane leakage from biogas production is included, the number will be 0,81
*** If the correction regarding methane leakage from biogas production is included, methane emissions from the waste sector decrease by 16%
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GREEN TRANSITION DENMARK
Agriculture Sector
The agriculture sector is the main contributor to Danish
methane emissions, with livestock accounting for almost
all methane emissions. Methane emissions from livestock
stem from enteric fermentation, which is the digestive
process in the rumen of ruminant animals, and manure
management, the methods used to handle animal
manure. The development in the agriculture sector has
been fairly stable since 1990, but the Danish climate
projections predict that methane emissions from
agriculture will decrease by 18% in 2030 compared to
2020. The projected decrease in methane emissions is
mainly due to an expected decrease in the number of
dairy cows and pigs, increased biogasification of cattle
and pig manure, the implementation of requirements for
frequent sluicing in pigsties from 2023, and the extraction
and extensification of agricultural land to reduce fertiliser
use
43
. It is important to mention that there is a great
uncertainty in the projections and measurements of
methane emissions in the agriculture sector because it is
difficult to quantify the complex biological processes.
As in other EU Member States, the Danish agricultural
sector is heavily dependent on the support it receives
from the European Union's Common Agricultural Policy
(CAP). However, a study of the CAP shows that 82% of the
EU’s agricultural subsidies are allocated to animal-based
food (38% directly and 44% for animal feed)
44
. This is
because the subsidy system is based on support per
hectare, which means that farms that use more land
receive more money. One of the main reasons why animal
production receives the largest share of agricultural
subsidies is that it takes up a lot of land to grow feed for
animals. The CAP architecture favors animal production
and makes it difficult to transform food production into
more sustainable and plant-based production. However,
an agriculture sector with less livestock and more plant-
based production would massively reduce methane
emissions from the sector.
Figure 10: Development of Danish Methane Emissions in the Agriculture Sector
45
8
7
6
5
4
3
2
1
0
1990
1993
1996
1999
2002
2005
2008
2011
2014
2017
2020
2023
mio. ton CO2e
TOTAL Agriculture Sector
Enteric fermentation
Manure management
15
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Enteric Fermentation
In 2023, enteric fermentation accounted for 62% of
methane emissions from livestock
46
. The metabolism of
feed in the rumen of ruminants leads to the formation of
methane. Methane emissions from enteric fermentation
in
ruminants
with
a
multi-chambered
stomach,
particularly dairy cows, are significantly higher than
emissions from production animals with a single stomach,
such as pigs
47
. This is clearly illustrated
in Figure 11,
which shows that cattle are responsible for the vast
majority of methane emissions from enteric fermentation.
Methane emissions from enteric fermentation can be
influenced by feeding practices and breeding and, most
importantly, by the number of ruminants. The Danish
government is adopting a requirement to reduce
emissions from livestock digestion that includes the use
of fodder with a high content of fat from 2025, which can
reduce
methane
emissions
from
dairy
cows.
Nevertheless, methane emissions per dairy cow are
expected to increase due to genetic improvement,
increased feed intake and optimised feed composition in
relation to production
48
. The expected decrease in
methane emissions from enteric fermentation is therefore
primarily driven by an expected decrease in the number
of dairy cows in Denmark.
Figure 11: Development of Methane Emissions from Enteric Fermentation
49
5
4
mio. ton CO2e
3
2
1
0
1990
1994
TOTAL
1998
Cattle
2002
2006
Sheep
2010
Swine
2014
Other livestock
2018
2022
16
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Feed additives and optimization are not enough
In the Danish debate on how to manage methane
emissions from the enteric fermentation of cows, the feed
additive ‘Bovaer’ is highlighted. This is because it is
estimated to reduce methane emissions from dairy cows
by around 30%. The effect of Bovaer is not included in the
ministry’s Climate Status and Projections 2024, but it is
expected to be included in the Climate Status and
Projections in 2025 if the climate effect is consolidated
50
.
It is important that the trade-offs of technologies are well
thought through before they are implemented on a large
scale.
In the case of Bovaer, the effect of the feed additive on
animal welfare has not been studied in-depth and studies
show that cows with high doses of Bovaer in their feed eat
less, which may be because the feed additive causes
discomfort to the cow
51
. At the same time, the use of
Bovaer risks keeping cows in barns with no or limited
grazing time that otherwise could have increased
biodiversity and nutrient cycling. Meanwhile, studies from
the Netherlands
52
and Sweden
53
show
that
methane
emissions from cattle can be reduced by approximately
30% if the animals only graze fresh grass and are not kept
and fed in barns. A Danish research project called
MetGraz is also investigating whether grazing cows emit
less methane than cows in barns, and preliminary results
show that this is the case
54
.
The trade-offs and side-effects of feed additives, as well
as other measures to optimize feed, need to be
considered. For example, palm oil is being used to
increase the fat content in cow feed, but this causes
deforestation in other parts of the world. As a result,
national emissions might drop, while they will rise
elsewhere, limiting net effect significantly – or removing it
entirely
55
. Therefore, feed optimization must consider the
global net effect as well as animal welfare concerns. An
alternative here could be Danish grown rapeseed, which
only has a third of the climate impact of imported palm oil.
Overall, to properly address methane emissions from
enteric
fermentation,
feed
additives
and
feed
optimization are important tools, but they are not enough.
A structural transformation of agriculture away from
industrial animal production towards plant-based food
production is necessary to limit the contribution to global
warming and ensure food production within planetary
boundaries. The total number of cows needs to be
reduced, as this will have a much larger impact on the
total methane emissions, and it will free up land for other
uses that previously was used for fodder.
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GREEN TRANSITION DENMARK
Manure Management
Methane
emissions
from
manure
management
Methane emissions from manure management can be
influenced by storage time, temperature, and manure
treatment technologies (e.g. biogas plants, more frequent
sluicing
or slurry cooling)
60
. The projected reduction in
methane emissions from manure management is
expected to be driven by the requirement of
frequent
sluicing in pigsties,
by extensification of agricultural land,
which reduces the use of manure, and by increased
biogasification
61
of cattle and pig manure. These
technologies are important in reducing methane
emissions from the agricultural sector, but it is
questionable whether technology alone can ensure that
we meet our climate targets. The unsustainable scale of
livestock production needs to be addressed if the targets
are to be met.
accounted for 38% of methane emissions from
agriculture in 2023
56
. Methane and nitrous oxides are
produced when manure is stored in barns and storage
facilities, but emissions vary depending on the amount
and type of manure and can be influenced by the way
manure is managed and stored in livestock buildings and
slurry tanks
57
. Especially cooling, acidification, and
biogasification reduces methane emissions.
Figure 12 illustrates
that manure management in pig
production accounts for most methane emissions from
manure management, followed by cattle production
58
.
While methane emissions from manure management in
pig production have decreased since they peaked in
2004, manure management in cattle production have
increased slightly since 1990, but remained more or less
stable since 2012, which is why the two types of
productions soon emit the same amount of methane. In
2030, methane emissions from manure management of
pig and cattle production are expected to be the same
59
.
Figure 12: Development of Methane Emissions from Manure Management
62
4
3
mio. ton CO2e
2
1
0
1990
1994
TOTAL
1998
Cattle
2002
2006
Sheep
2010
Swine
2014
2018
2022
Other livestock
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GREEN TRANSITION DENMARK
Waste Sector
Figure 13: Development of Danish Methane Emissions in the Waste Sector
63
2,0
1,8
1,6
1,4
mio. ton CO2e
1,2
1,0
0,8
0,6
0,4
0,2
-
1990
1993
1996
1999
2002
2005
2008
2011
2014
2017
2020
2023
Solid waste disposal
Anaerobic digestion at biogas facilities
Other waste
Waste composting
Wastewater Treatment and Discharge
TOTAL WASTE
In the waste sector, the two main sources of methane
emissions are solid waste disposal and anaerobic
digestion at biogas facilities. In 2023, solid waste disposal
accounted for 39% of methane emissions from the waste
sector, while anaerobic digestion at biogas facilities
accounted for
46%
64
.
The remaining 15% came from
composting (7%), anaerobic digestion at wastewater
facilities (3%), septic tanks (3%), sewage systems (1%),
and other waste (1%). Methane emissions from the waste
sector are expected to increase in the future, mainly due
to an increase in biogas production, which leads to an
increase in total methane emissions from anaerobic
digestion
65
.
However, if the expected effect of the earlier-
mentioned regulation (see page 12) on methane leakage
from biogas facilities, which was adopted in 2022, is
included, the overall methane emissions from the waste
sector will be reduced.
Anaerobic Digestion at Biogas Plants
Biogas plants use the process of anaerobic digestion,
where organic material (such as livestock manure) is
broken down by bacteria in an oxygen-free environment,
to produce biogas, which is a mix of mainly methane (CH4)
and carbon dioxide (CO2). The production of biogas is a
source of methane emissions due to leaks in the
processing plant and from the upgrading process, which
separates CH4 from CO2. In the future, biogas production
is expected to increase, leading to potentially higher
emissions from methane leakage. At the same time, the
above-mentioned new regulation on methane leakage
from biogas facilities, which requires biogas facilities to
minimise their methane leakage to less than 1%, which is
expected to reduce emissions. If this succeeds, emissions
from methane leakage from biogas facilities will decrease
despite increased biogas production
66
. However, the
methane leakages are not expected to be quantified until
2025, and there is still much uncertainty about the effects
of the regulation.
19
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Green Transition Denmark recommends close monitoring
of the new methane leakage regulation since additional
measures must be taken if a leakage of less than 1%
seems unfeasible with the current regulatory setup. Also,
quantifying methane leakage better will provide more
accurate greenhouse gas accounting.
In addition, Green Transition Denmark recommends that
the government lays out a strategy for expanding biogas
production targeted towards plant-based biomass, e.g.
side streams from industry, farms and household waste,
rather than manure. Since we need to reduce livestock
numbers, we must not create a lock-in to a certain
livestock production size by investing intensely in manure-
based biogas plants. The production of biogas in Denmark
is projected to increase from 22 PJ in 2022 to about 50
PJ in 2035
67
. Calculations from EA Energy made on
request of Greenpeace, show that it is possible to produce
50 PJ biogas in Denmark while simultaneously reducing
the number of livestock by 50%
68
. In addition, a report
from Green Transition Denmark shows that it is possible
to phase out the use of fossil energy by 2040 with the use
of only 42,3 PJ of biogas
69
.
Solid Waste Disposal
When organic waste deposited in e.g. landfills is broken
down by bacteria in an oxygen-free environment (the
process of anaerobic digestion mentioned above),
methane is produced. Methane emissions from landfills
have decreased significantly since 1990 because the
amount of organic waste going to landfills has decreased
over time, while organic waste in landfills naturally
degasses over time. One reason for the reduction in the
amount of organic waste going to landfill is the partial ban
on landfilling of organic waste introduced in 1997, which
means that most organic waste is now treated by
composting, incineration or biogasification
70
. However,
the decrease in emissions has stagnated in recent years
and is expected to remain at about the same level. One of
the reasons for this development is that the amount of
waste is expected to increase and that the disposed waste
degasses over time, according to the Climate Projection
71
.
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Energy Sector
Figure 14: Development of the Danish Methane Emissions in the Energy Sector
72
1,60
1,40
1,20
mio. ton CO2e
1,00
0,80
0,60
0,40
0,20
-
1990
1993
1996
1999
2002
2005
2008
2011
2014
2017
2020
2023
Energy Industries
Transport
Fugitive emissions from oil, gas and flaring
Manufacturing Industries and Construction
Other Sectors
TOTAL ENERGY
In the energy sector, the three main sources of methane
emissions are currently ‘fugitive emissions from fuels’,
‘energy industries’ and ‘other sectors’. In 2023, fugitive
emissions from extraction and distribution of fuels
accounted for 30%, energy industries for 30%, and other
sectors for 33%
73
. Methane emissions from the energy
sector are projected to decrease overall towards 2030,
due to reductions in methane emissions from public
electricity and heat supply, cars and residential buildings.
However, fugitive emissions from gas are projected to
increase towards 2030, accounting for 48% of methane
emissions from the energy sector in 2030
74
.
Energy Industries and Other Sectors
than the Danish consumption of piped gas, even though
fossil natural gas will still flow through the Danish gas
system, as it is part of the European gas network
76
.
Denmark should therefore replace the use of gas where
alternatives exist, e.g. electrification, even if the gas in the
pipelines is green gas in terms of inventory. A possible
surplus of Danish biogas could then be exported via the
European gas network to other countries where biogas will
replace the use of fossil natural gas - e.g. in Germany.
Other sectors that are responsible for methane emissions
within the energy sector are ‘residentials’ and ‘agriculture,
forestry and aquaculture’. While methane emissions from
‘agriculture, forestry and aquaculture’ are expected to
remain the same towards 2030, the emissions from
‘residentials’ are expected to decrease. Gas boilers in
households are an emitter of methane within this
category. The above-mentioned Climate Agreement from
2022 also sets the target that no residential buildings
should be heated with gas by 2035
77
. In 2023, 380.000
households were estimated to use a gas boiler as primary
heating system, and this number is estimated to decrease
to 130.000 in 2030 and to 110.000 in 2035
78
. This
21
Methane emissions from energy industries, which in the
Danish case is ‘public electricity and heat production’, are
expected to decrease towards 2030. One of the targets of
the Climate Agreement on green power and heat from
2022 is that all gas in Denmark should be green by 2030,
which means that district heating companies are required
to plan for the phasing out of fossil natural gas in the heat
production
75
.
However, this green gas target is defined as
being achieved when the production of biogas is higher
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GREEN TRANSITION DENMARK
means that the target of no gas heated residential
buildings in 2035 will not be achieved.
Gas in the heating sector should be phased out
used where there are no good alternatives, i.e. in certain
industries where high temperatures are required and for
peak loads in productions. This also means that biogas
should not be used in the heating sector, where better
alternatives are available.
In order to phase out gas heating in Danish households,
we also need a ban on the installation of new gas boilers
for heating. If this should be seen as violating EU single
market regulation, Denmark could instead put a high tax
on new gas boilers. When gas boilers are taken out, while
the owners are waiting for district heating pipes in their
local area, the utility company must provide them with an
intermediate solution, a second-hand boiler or an
intermediate heat pump solution.
Fugitive Emissions
In 2022, after the war broke out in Ukraine, the
government tried to step up its efforts to meet the target
of no gas heated residential buildings. The government
asked municipalities to inform owners of gas boilers
within a year whether they would be offered district
heating before 2028, and at the same time funding
schemes for heat pumps in residential buildings were set
up to encourage those who would not be offered district
heating to invest in heat pumps instead. But this attempt
was not successful, as the municipalities were not able to
complete the planning of the district heating pipelines
within the timeframe.
Despite the unsuccessful attempt, methane emissions
are projected to decrease due to an expected decrease in
consumption of piped gas, biogas and fossil natural gas,
as gas boilers are replaced by heat pumps or district
heating, and due to an expected increase in the share of
biogas in piped gas
79
. The same development is
estimated to apply for the gas used for space heating in
businesses.
Green Transition Denmark recommends that the use of
gas in the heating sector should be phased out by 2030
at the latest. This can be done by directing more planning
resources to municipalities. This will allow them to map
out whether owners of gas boilers will have access to
district heating or whether they will need to invest in heat
pumps.
In order to achieve the aforementioned goal of 100%
green gas in the Danish gas pipeline system, we must not
only expand biogas production, but also reduce gas
consumption overall. Biogas production must not be
expanded more than it is still possible to significantly
reduce the number of livestock animals to a sustainable
level, and we must continue to phase out the use of
energy crops in biogas plants
80
. Biogas should only be
Fugitive emissions from fuels and flaring are methane
leaks that occur during the extraction, production,
processing, storage, transmission and distribution of oil
and gas products
81
. In Denmark, the greatest contributors
of fugitive methane emissions are the platforms in the
North Sea that extracts oil and gas, as well as refineries
82
.
Fugitive emissions from oil and from flaring (controlled
burning of excess methane from oil and gas production
and refining) is projected to remain the same towards
2030, while fugitive emissions from gas are projected to
increase
83
.
Green Transition Denmark recommends that instead of
putting effort and resources into fixing pipes, which has a
smaller impact on methane emissions from oil, fossil
natural gas and energy production in general, effort and
resources should be put into the goal of phasing out the
production of oil and fossil natural gas. We can fix pipes
as an urgent measure to tackle fugitive methane
emissions, but this needs to be complemented by an end
date for the use of oil and gas. Green Transition Denmark
has presented a transformation scenario which shows
that it is possible to phase-out fossil energy in all parts of
society by 2040
84
. The scenario shows that it is possible
and economically responsible.
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Land Use, Land Use Change and Forestry (LULUCF)
In the Land Use, Land Use Change, and Forestry (LULUCF)
sector ‘grassland’ and ‘wetlands’ currently accounts for
most methane emissions. In 2023, grasslands and
wetlands each accounted for 35% of the sector’s
methane emissions, while forest land and cropland
accounted for 16% and 13% respectively
85
.
While
methane emissions from grassland, forest land, and
cropland decrease towards 2030, emissions from
wetlands increase. This means that wetlands are
projected to account for 73% of LULUCF’s methane
emissions in 2030. The implementation of policies that
facilitate the set-aside and rewetting of carbon-rich
agricultural land for the purpose of wetland restoration is
expected to result in a significant increase in the number
of wetlands
86
.
As mentioned earlier, methane emissions from wetlands
are defined as a natural source of emissions, and
wetlands also make a positive contribution by acting as
carbon sinks, regulating the water cycle and supporting
biodiversity. Furthermore, when peatlands are drained for
agriculture purposes, they emit large amounts of CO2.
Rewetting will therefore lead to a net reduction in
greenhouse gas emissions of 10-40 tons of CO2e per
hectare rewetted per year
87
. Therefore, increasing
methane emissions from this land use is not alarming.
Figure 15: Development of the Danish Methane Emissions in the LULUCF sector
88
0,35
0,30
0,25
mio. ton CO2e
0,20
0,15
0,10
0,05
-
1990
1993
1996
1999
2002
2005
Grassland
2008
2011
Wetlands
2014
2017
2020
2023
Forest land
Cropland
TOTAL LULUCF
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GREEN TRANSITION DENMARK
Conclusions
This paper has examined Danish methane emissions,
what the sources of methane emissions are, in which
sectors they are located, and how they are projected to
develop towards 2030. Table 2 shows which sources
account for the majority of methane emissions in
Denmark in 2020 and their projections to 2030. As shown
in this table, it is enteric fermentation and manure
management in the agriculture sector that account for the
vast majority of Danish methane emissions, should
therefore also be further addressed.
Therefore, the main focus must be on how to reduce
emissions from this sector. It is also important to address
methane emissions from the other sectors, where
reduction measures are available at a low or negative
cost. Biogas leakage in the waste sector and phasing out
oil and gas in the energy sector, including accelerating
phasing out gas boilers in Danish households
Table 2: The Largest Sources of Methane Emissions in Denmark*
89
(% of total methane emissions)
% in 2030 with methane
% in 2020
% in 2030
leakage from biogas
production correction
Energy Sector
Fugitive emissions from gas
1%
1%
2%
Enteric fermentation
Agriculture Sector
Manure management
46 %
48 %
51 %
35 %
26 %
28 %
LULUCF Sector
Wetlands
1%
5%
5%
Solid waste disposal
Waste Sector
Anaerobic digestion at biogas
facilities
**Methane leakage from biogas production is subtracted here.
5%
5%
5%
4%
9%
3 %
**
*Methane emissions that account for under 2% is removed from this table
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GREEN TRANSITION DENMARK
Green Transition Denmark's 9 Recommendations Elaborated
1. Develop a National Methane Action Plan with
a Reduction Target of 40-45%
3. Transition from Animal Production to Plant-
based Food Production
Denmark must develop a National Methane
Action Plan as soon as possible, with an
ambitious target of 40-45% by 2030 compared
to 2020. This reduction target is considered cost-
effective and feasible in the Global Methane
Assessment. And it is necessary because global
warming is approaching 1.5°C and methane
emissions, with their high short-term global
warming potential (GWP), will have a major
impact on whether we can keep the temperature
below 1.5°C.
2. Incorporate
the
Short-term
Perspective
The size of the Danish livestock production needs
to be reduced significantly as it accounts for the
vast majority of Danish methane emissions.
Transitioning to plant-based food production
systems will enable Denmark to become a net
producer of proteins
90
. Reducing livestock
production not only benefits the climate by
reducing methane emissions, but it also has a
number of other positive side-effects. To name
just a few, a reduction in livestock will lead to a
reduction
in
soybean
imports,
thereby
contributing positively to land use change
elsewhere in the world. The reduction will also
contribute positively to Danish land use, as
almost 80% of agricultural land is used to grow
animal feed
91
.
4. Consider
the
Trade-offs
of
the
Use
of
(GWP20) in the Decision-making
The short-term perspective (GWP20) must be
included in the plan of reaching the Danish
climate goal, as the deadline is within the next
20-25 years. Here reductions of methane
emissions play a particular important role. A 30%
reduction of methane emissions in 2030
compared to 2020 measured based on GWP100
will result in a reduction of 2.7 million tons of
CO2e, but if the reduction is measured based on
GWP20 the same 30% reduction will result in a
reduction of 8 million tons of CO2e. The use of
GWP20 takes into account the disproportionate
impact of methane on short-term temperature
and gives policymakers an incentive to focus on
reducing
methane
emissions
to
deliver
immediate climate benefits, slowing the rate of
global warming and buying time for longer-term
CO2 mitigation strategies.
Technologies Before They are Implemented
Some technologies can help reduce methane
emissions, but it is important to thoroughly
consider potential negative trade-offs. These
should be properly assessed before such
technologies are subsidized or implemented
through regulation. An example of this is the feed
additive Bovaer or the use of palm oil in feed, as
described above. The money invested in
technologies that lock-in current industrial
livestock production and leads to deforestation
and animal welfare issues, can be used better.
For example on documenting the potential effect
of grazing, which carries positive side-effects.
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GREEN TRANSITION DENMARK
5. Phase Out the Use and Production of Oil and
Gas
8. Biogas Should Only be Used Where There are
No Better Alternatives
Production of oil and fossil natural gas must be
phased out as soon as possible. We might repair
pipes as an urgent way of dealing with fugitive
methane emissions from production, but this
needs to be complemented by an end date for
the use of oil and gas. It is possible to achieve a
phase-out in 2040, which will have a significant
impact on reducing methane emissions from the
energy sector.
6. Advance the Target of a Phase-out of the Use of
Gas Boilers in Danish Households
The use of biogas must be prioritized for areas
where there are no alternatives, e.g. certain
industries that require high temperatures and for
peak load in the production. We need to use
biogas wisely so that it effectively replaces the
use of fossil natural gas. This means that it
should not be used in the heating sector where
alternatives are available.
9. Methane Leakage from Biogas Plants Must be
Addressed
Methane leakage from biogas plants must be
addressed to minimize emissions. The reduction
effect of the new methane regulation needs to be
closely monitored, as additional measures will
need to be taken if leakage of less than 1%
seems unachievable under the current regulatory
regime. In addition, the quantification of
methane leakage needs to be improved to
enable
more
accurate
greenhouse
gas
accounting.
Denmark must phase out gas (fossil natural gas
and biogas) for household heating by 2030.
Municipalities need more planning resources to
meet the 'Climate Agreement on Green Power
and Heat,' which aims to implement district
heating by 2028, providing a better alternative to
gas boilers in all households. To support this, a
ban on the purchase of gas boilers should be
introduced in 2025, as they typically last about
20 years. Given Denmark's goal of climate
neutrality by 2045, citizens should avoid
investing in gas boilers from 2025 to facilitate
the transition away from gas heating.
7. Biogas
Production
and
Use
must
be
Read more
Methane Matters:
https://methanematters.eu/
Energy within Planetary Boundaries:
https://rgo.dk/en/energi-inden-for-planetaere-
graenser/
From Feed to Food II:
https://rgo.dk/en/publication/from-feed-to-feed-in-
report/
Sustainable
Biogas is an important tool for addressing
climate, water and waste problems together, but
the production must be sustainable. This means
that the expansion of biogas production must be
in accordance with the need to reduce livestock
numbers significantly.
This report has been made with funding from the
Methane Matters Coalition. Green Transition
Denmark is a partner organisation of the Coalition.
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References
1.
2.
3.
4.
https://rgo.dk/wp-content/uploads/Ren-energi-indenfor-planetaere-graenser-i-2040.pdf
https://www.globalmethanepledge.org
https://www.globalmethanepledge.org/resources/global-methane-pledge
GMP participants + China who has stated that it will reduce its methane emissions as well, despite not being
a participant of the GMP.
https://green-alliance.org.uk/wp-content/uploads/2023/08/Why-the-UK-should-
do-more-to-cut-methane-emissions.pdf
https://www.globalmethanepledge.org/#pledges
https://www.unep.org/explore-topics/energy/facts-about-methane
https://www.ipcc.ch/report/ar6/syr/downloads/report/IPCC_AR6_SYR_LongerReport.pdf
https://methanematters.eu/wp-content/uploads/2024/07/Make-Methane-Matter_Final.pdf
https://www.ft.dk/samling/20191/almdel/kef/spm/492/svar/1701666/2263864.pdf
Calculated based on data from
https://www.kefm.dk/Media/638557759386656307/KF24_CRFtabels.xlsx
https://ing.dk/artikel/kronik-vi-undervurderer-temperatur-og-klimaeffekter-af-metanudledninger
https://www.eea.europa.eu/publications/methane-emissions-in-the-eu
https://www.eea.europa.eu/publications/methane-emissions-in-the-eu
https://methanematters.eu/wp-content/uploads/2024/07/Make-Methane-Matter_Final.pdf
https://www.unep.org/explore-topics/energy/facts-about-methane
https://global-tipping-points.org/download/4607/
https://global-tipping-points.org/download/4607/
https://www.iea.org/reports/methane-tracker-2021/methane-and-climate-change
https://www.wetlands.org/wetlands/
https://methanematters.eu
Charts made based on
https://methanematters.eu/wp-content/uploads/2024/07/Make-Methane-
Matter_Final.pdf
Data A:
https://www.ccacoalition.org/sites/default/files/resources/2021_Global-
Methane_Assessment_full_0.pdf
Data B:
https://www.ccacoalition.org/sites/default/files/resources//European%20Union%20Methane%20Action%2
0Plan.pdf
Made based on
https://methanematters.eu/wp-content/uploads/2024/07/Make-Methane-Matter_Final.pdf
With data from
https://www.eea.europa.eu/en/analysis/maps-and-charts/greenhouse-gases-viewer-data-
viewers
https://www.globalmethanepledge.org/annual-report/methane-plans-and-policies
https://www.ccacoalition.org/resources/national-methane-action-plans#
https://www.ccacoalition.org/resources/national-methane-action-plans
Global Methane Pledge, 2021
https://eur-lex.europa.eu/legal-content/EN/TXT/?uri=CELEX%3A52020DC0663
https://www.unep.org/explore-topics/energy/facts-about-methane
https://www.ccacoalition.org/sites/default/files/resources//European%20Union%20Methane%20Action%2
0Plan.pdf
https://www.ccacoalition.org/sites/default/files/resources//2021_Global-Methane_Assessment_full_0.pdf
https://www.ccacoalition.org/sites/default/files/resources/M-
RAP%20Roadmap%20Template%20Guidance%20-%20Working%20Final.pdf
Data from:
https://www.kefm.dk/Media/638557759386656307/KF24_CRFtabels.xlsx
https://www.eea.europa.eu/data-and-maps/data/data-viewers/greenhouse-gases-viewer
Data from (% is calculated by RGO):
https://www.kefm.dk/Media/638557759386656307/KF24_CRFtabels.xlsx
Data from:
https://www.kefm.dk/Media/638557759386656307/KF24_CRFtabels.xlsx
Data from:
https://www.kefm.dk/Media/638557759386656307/KF24_CRFtabels.xlsx
https://www.kefm.dk/klima/klimastatus-og-fremskrivning/klimastatus-og-fremskrivning-2024
https://www.kefm.dk/Media/638557749505615087/KF24%20Kapitel%2018%20Landbrugsarealer%20og
%20øvrige%20arealer.pdf
https://klimaraadet.dk/sites/default/files/imorted-file/bilagsrapport_om_lavbundsjorder_0.pdf
5.
6.
7.
8.
9.
10.
11.
12.
13.
14.
15.
16.
17.
18.
19.
20.
21.
22.
23.
24.
25.
26.
27.
28.
29.
30.
31.
32.
33.
34.
35.
36.
37.
38.
KEF, Alm.del - 2024-25 - Bilag 112: Henvendelse af 13/12-24 fra Rådet for Grøn Omstilling om Danske metan-udledninger og det globale metanløfte
2957298_0029.png
GREEN TRANSITION DENMARK
39.
https://klimaraadet.dk/sites/default/files/imorted-file/kulstofrige_lavbundsjorder_-
_analyse_af_klimaraadet_0.pdf
40.
https://oem.dk/media/awkfrkdz/1-klimaloesning-for-landbruget-mv_-a.pdf
41. Calculated based on GWP from:
https://www.ft.dk/samling/20191/almdel/kef/spm/492/svar/1701666/2263864.pdf
And data from:
https://www.kefm.dk/Media/638557759386656307/KF24_CRFtabels.xlsx
See Figure 2 for the projected greenhouse gas emissions in 2030 based on GWP100 and GWP20
42. Data from (% reduction is calculated by RGO):
https://www.kefm.dk/Media/638557759386656307/KF24_CRFtabels.xlsx
43.
https://www.kefm.dk/Media/638500583839358855/KF24%20Kapitel%2017%20Landbrugsprocesser.pdf
44.
https://www.nature.com/articles/s43016-024-00949-4
45. Data from:
https://www.kefm.dk/Media/638557759386656307/KF24_CRFtabels.xlsx
46. Calculated by RGO based on data from:
https://www.kefm.dk/Media/638557759386656307/KF24_CRFtabels.xlsx
47.
https://www.kefm.dk/Media/638500583839358855/KF24%20Kapitel%2017%20Landbrugsprocesser.pdf
48.
https://www.kefm.dk/Media/638500583839358855/KF24%20Kapitel%2017%20Landbrugsprocesser.pdf
49. Data from:
https://www.eea.europa.eu/en/analysis/maps-and-charts/greenhouse-gases-viewer-data-viewers
50.
https://www.ft.dk/samling/20231/almdel/mof/spm/506/svar/2034163/2842556/index.htm
51.
https://pure.au.dk/ws/portalfiles/portal/306097925/Rapport_FINAL_300123.pdf
52.
https://research.wur.nl/en/publications/enterische-methaanemissie-van-melkvee-in-relatie-tot-vers-graskwa
53.
https://jordbruksverket.se/jordbruket-miljon-och-klimatet/forskning-och-fakta-om-ekologisk-
produktion/arkiv/2023-06-13-betande-kor-kan-ge-mindre-metan-an-kor-pa-stall
54.
https://icoel.dk/klima/dansk-forskning-undersoeger-udledning-af-metan-fra-koeer-paa-graes/
55.
https://dcapub.au.dk/djfpublikation/djfpdf/DCArapport227.pdf
56. Calculated by RGO based on data from:
https://www.kefm.dk/Media/638557759386656307/KF24_CRFtabels.xlsx
57.
https://www.kefm.dk/Media/638500583839358855/KF24%20Kapitel%2017%20Landbrugsprocesser.pdf
58.
https://www.eea.europa.eu/en/analysis/maps-and-charts/greenhouse-gases-viewer-data-viewers
59.
https://www.kefm.dk/Media/638500583839358855/KF24%20Kapitel%2017%20Landbrugsprocesser.pdf
60.
https://www.kefm.dk/Media/638500583839358855/KF24%20Kapitel%2017%20Landbrugsprocesser.pdf
61. Biogas treatment of cattle and pig manure leads to lower methane emissions from the manure storage due
to an often shorter storage time before collection, and due to the emissions from the returned biogasified
manure are very low compared to non-biogasified manure
https://www.kefm.dk/Media/638500583839358855/KF24%20Kapitel%2017%20Landbrugsprocesser.pdf
62. Data from:
https://www.eea.europa.eu/en/analysis/maps-and-charts/greenhouse-gases-viewer-data-viewers
63. However, projections to 2030 show a decrease in methane emissions from anaerobic digestion in biogas
plants due to the above-mentioned regulation. The figure’s data come from:
https://www.kefm.dk/Media/638557759386656307/KF24_CRFtabels.xlsx
64. Calculated by RGO based on data from:
https://www.kefm.dk/Media/638557759386656307/KF24_CRFtabels.xlsx
65.
https://www.kefm.dk/Media/638557759386656307/KF24_CRFtabels.xlsx
66.
https://www.kefm.dk/Media/638500583600673372/KF24%20Kapitel%2024%20Produktion%20af%20oli
e,%20gas%20og%20VE-brændstoffer.pdf
67.
https://www.kefm.dk/Media/638500583600673372/KF24%20Kapitel%2024%20Produktion%20af%20oli
e,%20gas%20og%20VE-brændstoffer.pdf
68.
https://www.greenpeace.org/static/planet4-denmark-stateless/2023/01/e03557a9-
20221000_analyse_scenarier-for-biogas-mod-2030_ea-energianalyse.pdf
69.
https://rgo.dk/wp-content/uploads/Ren-energi-indenfor-planetaere-graenser-i-2040.pdf
70.
https://www.kefm.dk/Media/638501715568637065/KF24%20Kapitel%2026%20Øvrigt%20affald%20og%
20spildevand.pdf
71.
https://www.kefm.dk/Media/638501715568637065/KF24%20Kapitel%2026%20Øvrigt%20affald%20og%
20spildevand.pdf
72. Data from:
https://www.kefm.dk/Media/638557759386656307/KF24_CRFtabels.xlsx
73. Calculated by RGO based on data from:
https://www.kefm.dk/Media/638557759386656307/KF24_CRFtabels.xlsx
28
KEF, Alm.del - 2024-25 - Bilag 112: Henvendelse af 13/12-24 fra Rådet for Grøn Omstilling om Danske metan-udledninger og det globale metanløfte
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GREEN TRANSITION DENMARK
74. Calculated by RGO based on data from:
https://www.kefm.dk/Media/638557759386656307/KF24_CRFtabels.xlsx
75.
https://www.kefm.dk/aktuelt/nyheder/2022/jun/aftale-om-et-mere-groent-og-sikkert-danmark-
76.
https://www.ft.dk/samling/20231/almdel/kef/spm/414/svar/2055453/2879783.pdf
77.
https://www.regeringen.dk/nyheder/2022/aftale-om-et-mere-groent-og-sikkert-danmark/
78.
https://www.kefm.dk/klima/klimastatus-og-fremskrivning/klimastatus-og-fremskrivning-2024
79.
https://www.kefm.dk/klima/klimastatus-og-fremskrivning/klimastatus-og-fremskrivning-2024
80. From July 2024 maximum 4 % (by weight) of the feedstock to biogas plants can be energy crops (like maize,
beet, grain, and grass) and from 2025 it will no longer be permitted to use maize in biogas production -
https://ens.dk/ansvarsomraader/bioenergi/energiafgroeder-til-biogas
81.
https://www.kefm.dk/Media/638500583600673372/KF24%20Kapitel%2024%20Produktion%20af%20oli
e,%20gas%20og%20VE-brændstoffer.pdf
82.
https://dce.au.dk/udgivelser/vr/nr-451-500/nr-463-den-danske-emissionsopgoerelse-for-flygtige-
emissioner-fra-braendstoffer
83.
https://www.kefm.dk/klima/klimastatus-og-fremskrivning/klimastatus-og-fremskrivning-2024
84.
https://rgo.dk/en/energi-inden-for-planetaere-graenser/
85. Calculated by RGO based on data from:
https://www.kefm.dk/Media/638557759386656307/KF24_CRFtabels.xlsx
86.
https://www.kefm.dk/Media/638557749505615087/KF24%20Kapitel%2018%20Landbrugsarealer%20og
%20øvrige%20arealer.pdf
87.
https://klimaraadet.dk/sites/default/files/imorted-file/kulstofrige_lavbundsjorder_-
_analyse_af_klimaraadet_0.pdf
88. Data from:
https://www.kefm.dk/Media/638557759386656307/KF24_CRFtabels.xlsx
89. Calculated by RGO based on data from:
https://www.kefm.dk/Media/638557759386656307/KF24_CRFtabels.xlsx
90. At present, Denmark produces protein for about 16 mio. people annually, but imports protein equivalent to
the protein requirements of 23 mio. people. The current protein balance is therefore negative.
Source:
https://okologi.dk/media/owkjpddm/fftf2.pdf
91.
https://www.ft.dk/samling/20171/almdel/MOF/bilag/281/1858307.pdf
29