| Front page | | Contents | | Previous
| | Next |
Denmark's Third National Communication on Climate Change
5 Projections and the total effect of policies and measures
According to the EU's burdenssharing agreement, Denmark must reduce greenhouse gas
emissions by 21% in the period 2008-2012 in relation to the base year 1990/95 under the
Kyoto Protocol.
In connection with the agreement, Denmark took reservation in a declaration for the
effects of a large import of electricity from Norway and Sweden in the base year 1990,
which resulted in Denmark emitting 6.3 million tonnes CO2 less than would have
been the case if the electricity had been produced in Denmark. The Danish position was,
and is, that a fortuitous event such as a large electricity import in a single year should
not mean that Denmark's reduction obligation in relation to the EU should be calculated on
the basis of the random low emissions in 1990. In March 2002 Denmark had to accept a
Council decision that binds Denmark legally to a reduction of 21% in relation to the
emissions in the base year, which has not been adjusted for the electricity import.
Denmark was, however, assured in a political declaration from the EU Council of
Ministers and the European Commission that the assumptions relating to base year emissions
will be taken into account in connection with fixing the permitted amount of emissions in
2006, measured in tonnes of CO2 equivalents. The government will therefore work
to ensure that Denmark's reduction burden in 2008-2012 corresponds to 21% of the 1990
level adjusted for electricity import, corresponding to 5 million tonnes CO2
equivalents per year.
The shortfall in respect of fulfilling Denmark's obligations with the existing policies
and measures has been calculated partly for a situation in which account is taken of the
electricity import in 1990 and partly for a situation in which account is not taken of
this.
The projections are based on a number of sector-specific projections of the domestic
emissions for this period. These emissions depend on the scope of economic activity in all
sectors of society, energy prices, technological development and the legislation
regulating the various activities with respect to environment, energy efficiency, etc. The
main assumptions include the Ministry of Finance's estimate concerning economic
development1 and the IEA's expectations concerning future energy prices2. In addition, the
projections are based on already adopted regulation of various sectors, including the
environmental regulation of agriculture and the energy sector.
According to the latest inventories of greenhouse gas emissions, Denmark's reduction
obligation of 21% means that the emissions must be reduced from 69.5 million tonnes CO2
equivalents in the base year 1990/95 to 54.9 million in the period 2008- 2012.
The latest projections from February 2003 cover the period 2001-2017 and are reproduced
in Appendix B. However, the calculations for the period 2013 - 2017 must be described as
somewhat less certain than the projections up to 2013, in part because of the uncertainty
concerning the policies and measures and their expected effect increases with time. In
addition, new projections have not been carried out for the agricultural sector after
2012. The projection is a "with measures" projection that includes initiatives
that can be expected with reasonable certainty to be implemented without further political
action in the form of legislation, political agreements or similar. The projection must
therefore not be confused with the most probable development because it does not take
account of new political initiatives that could be taken according to the government's
climate strategy, February 2003, which was adopted by the Folketing on 13 March 2003. It
should be noted that the latest historical inventory of greenhouse gas emissions covers
the period 1990- 2001, for which reason the projection for 2001 in this report has been
replaced by the historical inventory for 2001.
Since this new inventory also includes an update of the 1990 figures as a consequence
of new knowledge, the base year - and thus also the shortfall - has been changed slightly
in relation to the inventory in the climate strategy.
Denmark's expected annual emissions in the period 2008-2012 have been calculated to be
80.1 million tonnes CO2 equivalents. As will be seen from table 5.1, the size
of the total greenhouse gas emissions depend greatly on CO2 emissions
associated with electricity export, which is estimated to be 9.9 million tonnes CO2
equivalents per year in the period 2008-2012.
Table 5.1.
Denmarks expected greenhouse gas emissions
Mill. tonnes CO2
equivalents |
Base
year 1990/951 |
2000 |
2001 |
"2010"2 |
"2015"3,4 |
CO2 |
(52.6*) 52.7 |
52.8 |
54.3 |
65.6 |
64.4 |
Methane (CH4) |
(5.8*) 5.7 |
5.8 |
5.6 |
5.0 |
4.7 |
Nitrous oxide (N2O) |
10.8 |
9.1 |
8.7 |
8.7 |
8.7 |
Industrial gases HFCs, PFCs, SF6 |
0.3 |
0.8 |
0.7 |
0.7 |
0.5 |
Total emissions |
(69.7*) 69.5 |
68.4 |
69.3 |
80.1 |
78.3 |
Kyoto objective: 21% |
|
|
|
(55.0*) 54.9 |
|
Shortfall |
|
|
|
(25.0*) 25.1 |
|
Electricity export (+)/import(-) |
-6.3 |
-0.3 |
|
+9.9 |
+9.1 |
Shortfall without electricity
export |
|
|
|
(15.1*) 15.2 |
|
|
* Note: The base-year data and shortfall
estimated in connection with the climate strategy are shown in brackets. |
1 |
The base year for CO2, methane and nitrous
oxide is 1990. In accordance with the Kyoto Protocol, 1995 has been selected as the base
year for the industrial gases. |
2 |
"2010" is used to express the average emissions
in the period 2008-2012. |
3 |
"2015" is used to express the average emissions
in the period 2013-2017 |
4 |
A new projection of agricultures emissions of
methane and nitrous oxide has not been carried out for the period 2013-2017. Here, the
emissions for the period 2008-2012 are kept. |
In this section the projection of the emissions of CO2, CH4 and N2O
from combustion of fuels and from gaseous emissions from fuels is described. The
projection includes all fuel-consuming sectors, including the transport sector and
industry. The projection is based on a projection of the development in energy consumption
in the period 2002-2017. The emissions of CO2, CH4 and N2O
have been calculated by multiplying the energy consumption by emission factors.
The projection of energy consumption is based on the initiatives described in sections
4.2.1 - 4.2.3 and 4.2.5 being implemented and on no further initiatives being implemented.
It should therefore be seen as a "with measures" projection. Figure 5.1 and
table 5.2 show the development of total energy consumption (excl. fuels for non-energy
purposes) with this assumption, broken down by sector.

Figure 5.1
Gross energy consumption 1990-2017, 1990-2001 observed
Source: Danish Energy Authority
In years with ample precipitation Denmark is a net importer of electricity produced at
Norwegian and Swedish hydropower stations, while in years with scanty precipitation, it is
a net exporter of electricity to Norway and Sweden. This has resulted in large
fluctuations in the observed Danish gross energy consumption in the period 1990-2001.
Table 5.2
Gross energy consumption 1990-2017, 1990 and 2001 are observed
PJ |
1990 |
2001 |
2005 |
2010 |
2015 |
Energy sector excl. electricity export |
377.4 |
398.8 |
406.9 |
435.1 |
421.6 |
- of which flaring |
4.2 |
10.8 |
10.1 |
10.1 |
9.4 |
Electricity export, net |
-67.7 |
4.1 |
123.7 |
119.0 |
112.9 |
Transport excl. international air
transp. |
141.6 |
164.0 |
174.9 |
187.0 |
192.4 |
Military transport |
1.6 |
1.3 |
2.0 |
2.0 |
2.0 |
Agriculture, etc. |
33.9 |
36.2 |
38.6 |
39.9 |
40.6 |
Industry and building |
98.7 |
95.0 |
100.8 |
110.6 |
118.8 |
Commerce and service |
21.2 |
15.7 |
16.5 |
17.3 |
17.9 |
Domestic sector |
85.2 |
83.9 |
82.1 |
S79.9 |
77.9 |
Total |
692.1 |
799.0 |
945.5 |
990.7 |
984.0 |
Total excl. electricity export |
759.8 |
794.9 |
821.8 |
871.7 |
871.1 |
Source: Danish Energy Authority

Figure 5.2
Gross energy consumption 1990-2017, 1990 and 2001 are observed
Energy consumption is expected to grow within most business sectors and transport in
the next 15 years, but to fall slightly in the domestic sector. The energy sector's
consumption has been calculated excluding fuels for production of electricity for export
because this consumption figures separately, but the calculation includes flaring.
Domestic electricity consumption is expected to grow, which is also reflected in the gross
energy consumption in the energy sector up to 2013. Thereafter, the sector's energy
consumption falls because a number of primary coalfired stations are expected to be
replaced by new, more efficient CHP plants, about half of which are expected to use
natural gas as fuel.
As will be seen, the big increase in total energy consumption in the first part of the
projection period is due to a big increase in electricity exports. This increase is
expected partly because the price of electricity on the Nordic electricity market is
expected to rise and partly because the existing national CO2 Quota Act for the
electricity sector only has an effect up to and including 2003. With that, it will be more
attractive for the electricity sector to export electricity.
Figure 5.2 shows the development of total energy consumption, broken down by fuels,
which determine the size of CO2 emissions because the fuels have very different
emission factors.
The increase in the quantity of renewable energy up to the year 2004 is due primarily
to expansion of wind turbines, while the increase in oil consumption can be attributed
mainly to growth in the transport sector. With the new power stations, natural gas
consumption increases from 2014 at the expense of coal consumption. This change means a
reduction in CO2 emissions because natural gas has far lower emission factors
than coal.
As will be seen later, with the expected development of energy consumption the CO2
emissions from Danish territory will exceed the Kyoto objective for 2008-2012. An EU
Directive on trading with CO2 emissions from electricity and heat production,
together with fuel consumption in certain sectors of industry, is expected to play a vital
role in costeffective achievement of Denmark's Kyoto target. Table 5.3 shows the resulting
emissions of CO2, CH4 and N2O from the energy sector in
the "with measures" projection. The emissions of CH4 and N2O
calculated as 1000 tonnes are CO2 equivalents. Appendix B contains detailed
tables showing the results of the projections.
Table 5.3
"With measures" projection, 1990-2001 observed
Greenhouse gas
emissions in 000 tonnes CO2 equivalents |
1990 |
2000 |
2001 |
2005 |
2010 |
2015 |
CO2 combustion of
fuels |
|
|
|
|
|
|
Energy production |
26202 |
25121 |
26375 |
33629 |
35401 |
32986 |
Industry and building &
construction |
5605 |
5823 |
5909 |
6454 |
7121 |
7687 |
Transport |
10381 |
12046 |
12174 |
13098 |
13977 |
14366 |
Other sectors (commerce and service,
households and agriculture, forestry and fishery) |
8959 |
7505 |
7688 |
7380 |
7359 |
7290 |
Other |
119 |
111 |
97 |
230 |
223 |
217 |
CO2
gaseous emission from fuels |
|
|
|
|
|
|
Flaring |
240 |
593 |
633 |
573 |
573 |
537 |
CO2
total emission from energy and transport |
51530 |
51199 |
52779 |
61134 |
64431 |
62865 |
CH4
total emission from energy and transport |
273 |
763 |
807 |
889 |
866 |
832 |
N2O
total emission from energy and transport |
583 |
797 |
831 |
1103 |
1197 |
1177 |
Total greenhouse gas emission from
energy and transport |
52386 |
52728 |
54416 |
63126 |
66495 |
64874 |
Source: 1990-2001: National Emission Report (NIR), National
Environmental Research Institute, April 2003, 2002-2017: Environmental Project No. 764,
Danish Environmental Protection Agency, February 2003 and Danish Energy Agency
Besides the greenhouse gas emissions mentioned in section 5.2, industrial processes
include a number of activities that emit greenhouse gases. This section covers emissions
connected with production of cement, chalk and bricks, together with emissions of the
industrial gases HFCs, PFCs and SF6.
The projection of the emissions is based on implemented and adopted policies and
measures, described in chapter 4, including a statutory order on phasing out certain
industrial gases. This statutory order will result in a reduction in greenhouse gas
emissions of, on average, 1.1 million CO2 equivalents per year in the period
2008-2012. It is covered by a ban on the use of HFC as a coolant in the retail trade and
stationary A/C systems from 1 January 2007, except for refilling of existing systems, and
as a foaming agent in PUR foam from 1 January 2006.
16% of Denmark's greenhouse gas emissions in 2001 consists of methane and nitrous
oxide, which are primarily emitted by agriculture. The methane and nitrous oxide emissions
are not taxed and are only regulated indirectly via the regulation of the effect on the
aquatic environment of nitrogen losses from agriculture, e.g. in the Action Plan for the
Aquatic Environment II. Further possibilities for reduction of the methane and nitrous
oxide emissions in the agricultural sector have not been sufficiently identified at
present. More knowledge is needed on both technical possibilities for reduction and the
associated costs.
Owing to the EU's milk quotas and the increasing productivity within dairy farming, the
cattle population is expected to fall by 1.8% per year to 524,000 dairy cows in 2010. In
pig farming, on the other hand, production is expected to rise by 1.5 % per year. This
will result in increased production of fatteners to just over 26 million in 2010. In
total, the fall in cattle population and the rise in pig population are expected to result
in a small increase in the total quantity of manure.
Total agricultural land is expected to fall by 0.3% per year. In addition, the planned
afforestation area has been deducted. It is also assumed that agricultural land used for
organic farming will reach 220,000 ha in 2010. The area with set-aside crops according to
the EU's subsidy schemes is estimated to be 7% of the total agricultural area in the
entire projection period.
Increasing productivity of individual cows means a rise in the emissions
coefficient for methane from dairy cows from 102 kg methane/cow/year in 1990 to 117 kg
methane/cow/year in 2010. However, this is more than balanced by the fall in the
population of dairy cows, and the result is a fall in methane emissions (table 5.6).
The fall in nitrous gas emissions shown in table 5.7 can be attributed particularly to
reduced use of nitrogen fertilisers and a fall in nitrogen leaching and ammonia
evaporation, which are effects of the action plans for the aquatic environment area. It is
assumed that the aquatic environment action plans (Action Plans for the Aquatic
Environment I and II) will be fully implemented in 2003.
Table 5.4
Industrial greenhouse gas emissions (HFCs, PFCs and SF6),
1990-2001 observed.
1000 tonnes CO2
equivalents |
1995 |
2000 |
2001 |
2005 |
2010 |
2015 |
2020 |
HFCs, PFCs and SF6 |
344 |
793 |
700 |
808 |
702 |
507 |
230 |
|
|
Source: |
1990-2001: National Emission Report (NIR), National
Environmental Research Institute, April 2003, 2002-2017: Environmental Project No. 764,
Danish Environmental Protection Agency, February 2003 |
Table 5.5
Emissions from cement, chalk and brick production, 1990-2001 observed
1000 tonnes CO2 |
1990 |
2000 |
2001 |
2005 |
2010 |
2015 |
Cement, chalk and brick production |
1005 |
1453 |
|
1456 |
1458 |
1420 |
|
|
Source: |
1990-2001: National Emission Report (NIR), National
Environmental Research Institute, April 2003, 2002-2017: Environmental Project No. 764,
Danish Environmental Protection Agency, February 2003 |
Table 5.6
Methane emissions from agriculture in the period 1990 to 2015, 1990-2000
observed
1000 tonnes CO2
equivalents |
1990 |
2000 |
2001 |
2005 |
2010 |
2015 |
Enteric Fermentation |
3189 |
2715 |
2747 |
2641 |
2509 |
2459 |
Manure Management |
900 |
861 |
884 |
707 |
690 |
674 |
Total Methane Emissions |
4089 |
3575 |
3632 |
3348 |
3199 |
3133 |
|
|
Source: |
1990-2001: National Emission Report (NIR), National
Environmental Research Institute, April 2003, 2002-2017: Environmental Project No. 764,
Danish Environmental Protection Agency, February 2003 |
Table 5.7
Nitrous oxide emissions from agriculture in the period 1990 to 2015
1000 tonnes CO2
equivalents |
1990 |
2000 |
2001 |
2005 |
2010 |
20151 |
Nitrous oxide from agriculture, total |
10259 |
8293 |
7918 |
7501 |
7553 |
7553 |
|
|
1. |
Calculations have not been carried out of the emissions
within the agricultural sector after the first obligation period 2008-2012. |
Source: |
1990-2001: National Emission Report (NIR), National
Environmental Research Institute, April 2003, 2002-2017: Environmental Project No. 764,
Danish Environmental Protection Agency, February 2003 |
The projections for CO2 sequestration in forests are based on an assumption
that the present subsidy structure and financing are maintained until the end of 2012. So
far, financing has been made available until the end of 2003, and political commitment for
public financing and/or access to alternative sources of financing for private
afforestation may be available even beyond 2003. Table 5.8 shows the expected rate of
afforestation in selected years up to 2020. Indeed, the rate of private afforestation will
depend on the economic conditions in the agricultural sector, and, as the marginal
agricultural localities are planted over time, a saturation point may be reached where the
existing subsidies no longer provide an incentive for further afforestation.
The objective of the waste plan - Waste 21 - is to reduce the proportion of waste going
to landfill sites from 2.1 million tonnes (16%) in 1997 to 1.5 million tonnes (12%) in
2004. As mentioned earlier, this target was already achieved in 2000. The net methane
emissions (produced methane less recovered methane) from Danish landfill sites is
calculated to be 62,400 tonnes in 1990, rising to 65,500 tonnes in 1994 and then steadily
falling to 38,900 tonnes in 2012. The average annual net methane emissions from landfill
sites in 2008-2012 correspond to about 0.9 million tonnes CO2 equivalents.
There are no emissions of methane from wastewater in Denmark because wastewater is treated
with aerobic processes.
Table 5.8
Afforestation area and CO2 sequestration since 1990 and forecasts for
selected years over the next 20 years3
Look here!
Table 5.9
Methane emissions from landfill sites in the period 1990 to 2012, 1990-2001
observed.
Tonnes methane, CH4. |
1990 |
2000 |
2001 |
2005 |
2010 |
Methane emissions from landfill sites
(gross) |
64,000 |
67,800 |
67,000 |
61,200 |
57,700 |
Recovery of methane from landfill
sites |
1,700 |
10,800 |
10,000 |
11,400 |
9,700 |
Methane emissions from landfill
sites (net) |
62,400 |
57,500 |
57,000 |
49,800 |
45,000 |
|
|
Source: |
1990-2001: National Emission Report (NIR), National
Environmental Research Institute, April 2003, 2002-2017: Environmental Project No. 764,
Danish Environmental Protection Agency, February 2003 |
Table 5.9 shows the expected development of CO2 emissions, while Appendix B
gives a more detailed projection. The biggest source of CO2 emissions in
Denmark is combustion of fossil fuels, including electricity and heat production and
transport. The transport sector has had the biggest increase in CO2 emissions
since 1990, and the emissions are expected to continue rising for the whole of the
projection period. The CO2 emissions from the transport sector were 10,404 Gg
in 1990 and rose to 12,077 Gg in 2001, while in the period 2008-2012 it has been
calculated that the average annual CO2 emissions will be 13,727 Gg. The
emissions from energy production, including conversion and distribution, fluctuated in the
period 1990- 2001 due to greatly varying electricity export/import. The CO2
emissions from energy production were 26,202 Gg in 1990 and 26,375 Gg in 2001, while for
the period 2008-2012 it has been calculated that the average annual CO2
emissions will be 35,405 Gg, of which 9,900 Gg can be attributed to electricity production
for export.
Table 5.10
Projection of Denmarks CO2 emission 2000-2017 and observed
emission in 1990, 2000 and 2001
|
1990 |
2000 |
2001 |
2005 |
2008-12 |
2013-17 |
Greenhouse gas source and sink categories |
(Gg CO2) |
1. Energy |
51530 |
51199 |
52779 |
61134 |
64394 |
63370 |
A Fuel Combustion Activities (Sectoral
Approach) |
51290 |
50606 |
52145 |
60561 |
63821 |
62822 |
1 Energy Industries |
26202 |
25121 |
26375 |
33629 |
35405 |
33475 |
2 Manufacturing Industries and
Construction |
5605 |
5823 |
5909 |
6454 |
7111 |
7681 |
3 Transport |
10404 |
12046 |
12077 |
12869 |
13727 |
14153 |
4 Other Sectors |
8959 |
7505 |
7688 |
7380 |
7355 |
7295 |
5 Other (Here: Military mobile and in
projections other off road) |
119 |
111 |
97 |
230 |
223 |
217 |
B Fugitive Emissions from Fuels |
240 |
593 |
633 |
573 |
573 |
548 |
1 Solid Fuels |
0 |
0 |
0 |
0 |
0 |
0 |
2 Oil and Natural Gas |
240 |
593 |
633 |
573 |
573 |
548 |
2. Industrial Processes |
1005 |
1453 |
1464 |
1456 |
1458 |
1420 |
3. Solvent and Other Product Use |
124 |
112 |
112 |
60 |
68 |
68 |
4. Agriculture |
0 |
0 |
0 |
0 |
0 |
0 |
5. Land-Use Change and Forestry
(LUCF) |
-3118 |
-3517 |
-3531 |
-1063 |
-1199 |
-1360 |
6. Waste |
0 |
0 |
0 |
0 |
0 |
0 |
7. Other |
0 |
0 |
0 |
0 |
0 |
0 |
Total Emissions/Removals with LUCF |
49541 |
49247 |
50824 |
61587 |
64722 |
63499 |
Total Emissions without LUCF |
52659 |
52764 |
54355 |
62650 |
65921 |
64859 |
|
|
|
|
|
|
|
Memo Items: |
|
|
|
|
|
|
International Bunkers |
4857 |
6629 |
5983 |
6376 |
6835 |
7321 |
Aviation |
1762 |
2348 |
2378 |
2758 |
3218 |
3704 |
Marine |
3095 |
4281 |
3605 |
3618 |
3618 |
3618 |
Multilateral Operations |
0 |
0 |
0 |
0 |
0 |
0 |
CO2 Emissions from Biomass |
4611 |
7001 |
7679 |
0 |
0 |
0 |
|
|
Source: |
1990-2001: National Emission Report (NIR), National Environmental
Research Institute, April 2003, 2002-2017: Environmental Project No. 764, Danish
Environmental Protection Agency, February 2003 |
The total CO2 emissions without land-use change and forestry (LUCF) was 52,659
Gg in 1990 and 54,355 Gg in 2001, while for the period 2008-2012 it has been calculated
that the average annual CO2 emissions will be 65,921 Gg.
CH4
Most of the methane emissions come from farm animals' digestive systems. The reduced
emissions from 1990 to 2001 and continued reduction in the projection period can be
attributed mainly to a smaller cattle population. The second-largest source of methane
emissions are landfill sites, where emissions also decreased from 1990 to 2001. However,
the energy sector's methane emissions increased considerably in the same period due to
increased use of gas engines. Total methane emissions were 5,672 Gg CO2
equivalents in 1990 and 5,606 CO2 equivalents in 2001, while in the period
2008-2012, is has been calculated that the average annual emissions will be 4,979 CO2
equivalents.
Table 5.11
Projection of Denmarks methane emissions 2002-2017, 1990-2001 observed
|
1990 |
2000 |
2001 |
2005 |
2008-12 |
2013-17 |
Greenhouse gas source and sink categories |
(CH4
in Gg CO2 equivalent) |
Total Emissions |
5672 |
5535 |
5606 |
5281 |
4979 |
4656 |
1. Energy |
273 |
763 |
807 |
889 |
866 |
839 |
A Fuel Combustion Activities
(Sectoral Approach) |
180 |
625 |
660 |
612 |
585 |
569 |
1 Energy Industries |
1 |
4 |
3 |
17 |
17 |
14 |
2 Manufacturing Industries and
Construction |
17 |
38 |
40 |
32 |
34 |
36 |
3 Transport |
0 |
0 |
0 |
0 |
0 |
0 |
4 Other Sectors |
0 |
0 |
0 |
0 |
0 |
0 |
5 Other (Here: Military mobile and in
projections other off road) |
0 |
0 |
0 |
1 |
1 |
1 |
B Fugitive Emissions from Fuels |
93 |
138 |
147 |
276 |
281 |
270 |
1 Solid Fuels |
72 |
64 |
69 |
97 |
101 |
91 |
2 Oil and Natural Gas |
0 |
0 |
0 |
0 |
0 |
0 |
2. Industrial Processes |
0 |
0 |
0 |
0 |
0 |
0 |
3. Solvent and Other Product Use |
0 |
0 |
0 |
0 |
0 |
0 |
4. Agriculture |
4089 |
3575 |
3632 |
3348 |
3200 |
3133 |
A. Enteric Fermentation |
3189 |
2715 |
2747 |
2641 |
2509 |
2459 |
B. Manure Management |
900 |
861 |
884 |
707 |
690 |
674 |
5. Land-Use Change and Forestry
(LUCF) |
0 |
0 |
0 |
0 |
0 |
0 |
6. Waste |
1310 |
1197 |
1168 |
1045 |
914 |
684 |
1 Managed Waste Disposal on Land |
1310 |
1197 |
1168 |
1045 |
914 |
684 |
7. Other |
0 |
0 |
0 |
0 |
0 |
0 |
|
|
Source: |
1990-2001: National Emission Report (NIR), National
Environmental Research Institute, April 2003, 2002-2017: Environmental Project No. 764,
Danish Environmental Protection Agency, February 2003 |
N2O
Agriculture is by far the biggest source of emissions of nitrous oxide because this can
form in soil through bacterial conversion of nitrogen in fertiliser and manure spread on
fields. The main reason for the reduction in total nitrous oxide emissions from 10,843 Gg
CO2 equivalents in 1990 to 8,749 Gg CO2 equivalents in 2001 is a
combination of the Action Plans for the Aquatic Environment I and II and the Action Plan
for Sustainable Agriculture. In the period 2008-2012 calculations indicate average annual
emissions of 8,738 CO2 equivalents. The contribution from the transport sector
and the energy sector to nitrous oxide emissions is expected to rise, while the
contribution from agriculture is expected to fall slightly in relation to 2001.
SF6
In accordance with the possibilities offered in the Kyoto Protocol, Denmark has chosen
1995 as the base year for emissions of the industrial gases HFCs, PFCs and SF6.
The total emissions of these gases were 344 Gg CO2 equivalents in 1995 but
double that - 793 Gg CO2 equivalents - in 2000. In 2001 the emissions fell to
700 CO2 equivalents.
Table 5.12
Projection of Denmarks nitrous oxide emissions 2002-2017, 1990-2001
observed
|
1990 |
2000 |
2001 |
2005 |
2008-12 |
2013-17 |
Greenhouse gas source and sink categories |
(N2O
in Gg CO2 equivalent) |
Total Emissions |
10843 |
9090 |
8749 |
8604 |
8738 |
8738 |
1. Energy |
583 |
797 |
831 |
1103 |
1191 |
1185 |
A Fuel Combustion Activities
(Sectoral Approach) |
582 |
793 |
827 |
1101 |
1190 |
1184 |
1 Energy Industries |
275 |
263 |
280 |
358 |
374 |
340 |
2 Manufacturing Industries and
Construction |
54 |
57 |
57 |
61 |
67 |
72 |
3 Transport |
147 |
379 |
393 |
592 |
658 |
681 |
4 Other Sectors |
106 |
93 |
95 |
88 |
88 |
88 |
5 Other (Here: Military mobile and in
projections other off road) |
1 |
1 |
2 |
2 |
2 |
2 |
B Fugitive Emissions from Fuels |
1 |
3 |
3 |
2 |
2 |
2 |
1 Solid Fuels |
0 |
0 |
0 |
0 |
0 |
0 |
2 Oil and Natural Gas |
1 |
3 |
3 |
2 |
2 |
2 |
2. Industrial Processes |
0 |
0 |
0 |
0 |
0 |
0 |
3. Solvent and Other Product Use |
0 |
0 |
0 |
0 |
0 |
0 |
4. Agriculture |
10259 |
8293 |
7918 |
7501 |
7547 |
7553 |
A. Enteric Fermentation |
462 |
440 |
442 |
723 |
747 |
750 |
B. Manure Management |
9797 |
7853 |
7477 |
6779 |
6800 |
6803 |
5. Land-Use Change and Forestry
(LUCF) |
0 |
0 |
0 |
0 |
0 |
0 |
6. Waste |
0 |
0 |
0 |
0 |
0 |
0 |
7. Other |
0 |
0 |
0 |
0 |
0 |
0 |
|
|
Source: |
1990-2001: National Emission Report (NIR), National
Environmental Research Institute, April 2003 2002-2017: Environmental Project No. 764,
Danish Environmental Protection Agency, February 2003 |
Table 5.13
Projection of Denmarks industrial gas emission 2002-2017, 1990, 2000 and 2001
observed
|
1995 |
2000 |
2001 |
2005 |
2008-12 |
2013-17 |
Greenhouse gas source and sink categories |
(HFCs, PFCs
and SF6 in Gg CO2 equivalent) |
Total Emissions of HFCs, PFCs and SF6 |
344 |
793 |
700 |
809 |
706 |
497 |
2. Industrial Processes |
344 |
793 |
700 |
809 |
706 |
497 |
C Metal Production |
36 |
21 |
0 |
0 |
0 |
0 |
1 Iron and Steel Production |
0 |
0 |
0 |
0 |
0 |
0 |
2 Ferroalloys Production |
0 |
0 |
0 |
0 |
0 |
0 |
3 Aluminium Production |
0 |
0 |
0 |
0 |
0 |
0 |
4 SF6 Used in Aluminium and
Magnesium Foundries |
36 |
21 |
0 |
0 |
0 |
0 |
SF6 Used in Aluminium
Foundries |
0 |
0 |
0 |
0 |
0 |
0 |
SF6 Used in Magnesium
Foundries |
36 |
21 |
0 |
0 |
0 |
0 |
5 Other |
0 |
0 |
0 |
0 |
0 |
0 |
F Consumption of Halocarbons and
Sulphur Hexafluoride |
308 |
771 |
700 |
809 |
706 |
497 |
1 Refrigeration and Air Conditioning
Equipment |
55 |
551 |
468 |
576 |
541 |
338 |
2 Foam Blowing |
182 |
166 |
186 |
206 |
115 |
55 |
3 Fire Extinguishers |
0 |
0 |
0 |
0 |
0 |
0 |
4. Aerosols/ Metered Dose Inhalers |
0 |
14 |
12 |
0 |
0 |
0 |
5 Solvents |
0 |
0 |
0 |
0 |
0 |
0 |
6. Semiconductor Manufacture |
0 |
0 |
0 |
0 |
0 |
0 |
7. Electrical Equipment (SF6) |
4 |
11 |
13 |
12 |
14 |
15 |
8 Other |
68 |
29 |
22 |
15 |
37 |
89 |
C3F8 (PFC used as detergent) |
0 |
2 |
4 |
0 |
0 |
0 |
SF6 (Window plate
production, research laboratories and running shoes) |
68 |
27 |
18 |
15 |
37 |
89 |
|
Total Emissions of HFCs |
236 |
705 |
647 |
764 |
638 |
374 |
Total Emissions of PFCs |
1 |
28 |
22 |
17 |
18 |
19 |
Total Emissions of SF6 |
107 |
59 |
30 |
27 |
50 |
104 |
|
|
Source: |
1990-2001: National Emission Report (NIR), National
Environmental Research Institute, April 2003, 2002-2017: Environmental Project No. 764,
Danish Environmental Protection Agency, February 2003 Environmental Project No. 761,
Danish Environmental Protection Agency, February 2003 |
Table 5.14
Greenlands actual CO2 emissions from combustion of fossil
fuels and expected CO2 emissions from electricity and district heat production
Year |
1990 |
1995 |
2000 |
2003 |
2005 |
2008 |
2009 |
2010 |
2011 |
CO2 emission from
combustion of fossil fuels (1000 tonnes) |
626 |
525 |
661 |
|
|
|
|
|
|
Of which CO2 emissions from
electricity and district heat production in towns and villages (1000 tonnes) |
|
125* |
135 |
137 |
136 |
126 |
121 |
121 |
121 |
Source: Nukissiorfiit.
The main reasons for this were the introduction of a tax and legislation on phasing out
import, production, and use of these gases. For the period 2008-2012 calculations indicate
total average annual industrial gas emissions of 706 CO2 equivalents.
Thereafter, a considerable reduction is expected in HFCs, which are the largest
contributor to industrial gas emissions, and overall this will result in a considerable
reduction of industrial gas emissions after the first commitment period.
With respect to the expectations concerning future greenhouse gas emissions in
Greenland, the projections cover only electricity and district heat production.
The projections for CO2 emissions from electricity and district heat
production are based on a projected increase in energy consumption of 1% up to 2005 and
then stagnation. The projections are also based on the fact that a hydropower station is
under construction and expected to go into operation in 2004 and that a further hydropower
station is planned, which will go into operation in 2006. There are not at the present
time any estimates of future greenhouse gas emissions on the Faroe Islands.
The projection of energy consumption in the business sector and the public service
sector is based on an ADAM/EMMA projection, while the domestic sector is projected on the
basis of the bottom-up principle.
EMMA is a macro model that describes the final energy consumption broken down into a
number of sectors and seven types of energy. It is based on historical experience with the
behaviour of businesses and households and is documented in satellite models for ADAM,
NERI Technical Report No. 148, DMU 1995.
In EMMA, energy consumption in the business sector is determined by three factors:
production, energy prices/taxes and energy efficiencies/ trends. Increased production will
increase the demand for energy input, whereas increased energy prices and taxes will pull
in the direction of a more limited demand for the fuels. Improved energy efficiency will
mean that production can be maintained using less energy, and in EMMA this results in
reduced energy consumption.
The projection of production is based on the ADAM projection in the Economic Report,
January 2002, covering the period 2000-2010. For the period 2011-2017 figures from the
Financial Report 2001 have been used.
The domestic sector's energy consumption has been determined using the bottom-up
models: the Electricity model for households and the Heating model for households. The
projection is based on, among other things, expectations concerning growth in the housing
stock and expectations concerning the development in the number of electric appliances.
The projection of electricity and heat production is based on the Danish Energy
Authority's RAMSES model, using as the basis the demand for electricity and district heat
according to the projection of the consumption sectors. In the projection, electricity and
heat production is divided between existing and possible new production plants on the
basis of technical and economic parameters. Industrial and local mini-CHP production is
not projected in the RAMSES model so a separate (bottomup) projection has been made of
this production.
Table 5.15
Average annual rate of growth in real production value of business in % in relation to
the previous year
Look here!
The projection of road transport, rail transport, domestic ferries and freighters,
together with domestic air transport is documented in the report "The transport
sector's energy consumption and emissions", Danish Road Directorate, 2002. The
projection is based on, among other things, the same economic assumptions as the EMMA
projection above.
The armed forces' consumption of transport energy is kept at a level corresponding to
the average for 1998-2001. International shipping and border trade with diesel are kept at
the 2001 level.
Tables 5.14, 5.15 and 5.16 show a number of key figures and key assumptions for the
projection.
Additional information on the methods used in the projections is available in
Environmantal Project No 764, published by the Danish Environmental Protection Agency in
February 2003.
Table 5.16
Development of energy prices, excl. taxes, deflated
Look here!
Table 5.17
Index of growth in households and housing unit area in Denmark
Year |
Households |
Housing unit area |
2001 |
100 |
100 |
2005 |
102 |
102 |
2012 |
106 |
107 |
2030 |
114 |
117 |
|
|
1 |
Economic Report, Ministry of Finance, January 2002, and
Financial Report 2001 from the Ministry of Finance |
2 |
World Energy Outlook 2002, IEA |
3 |
The forecast is based on afforestation continuing as
hitherto up to 2012. |
| Front page | | Contents | | Previous
| | Next | | Top
| |
|