COMMISSION OF THE EUROPEAN COMMUNITIES 
Brussels, 14.03.1996 
COM(96) 91 final 
REPORT FROM THE COMMISSION 
under Council Decision 93/389/EEC 
SECOND EVALUATION OF NATIONAL PROGRAMMES UNDER THE MONITORING 
MECHANISM OF COMMUNITY C02 AND OTHER GREENHOUSE GAS EMISSIONS 
Progress Towards the Community C02 Stabilisation Target 

CONTENTS 
1 INTRODUCTION \ 
1.1 THE MONITORING MECHA NISM A ND THE SECOND EVA L VA TION REPOR T 1 
1.2 THE COMMUNITY TARGET 2 
2 GREENHOUSE GAS INVENTORIES 4 
2.1 COMMUNITY INVENTORIES 4 
2.2 REMOVAL BY SINKS 8 
2.3 CONCLUSIONS 8 
3 EVALUA TION OF PROGRESS TOWARDS THE TARGET 9 
3.1 CONTENT OF NATIONAL PROGRAMMES 9 
3.2 CO2 LIMITATION STRATEGIES IN THE COMMUNITY 10 
3.3 TRAJECTORIES AND EFFECTS OF MEASURES 12 
4 CONCLUSIONS 20 
ANNEX A TABLES SHOWING C02 INVENTORIES, TRAJECTORIES AND 
EFFECTS OF MEASURES FOR THE 15 MEMBER STATES 
ANNEX B COUNTRY SUMMARIES 
INTRODUCTION 
1.1 THE MONITORING MECHANISM AND THE SECOND EVALUA TION REPORT 
In the Monitoring Mechanism decision (1), the Commission is requested to report on an annual 
basis to the Council and the European Parliament, on whether progress in the Community as a 
whole is sufficient to ensure stabilisation of C02 emissions by 2000 at 1990 levels. This 
objective was agreed at the joint Energy/Environment Council of 29 October, 1990. The first 
evaluation was carried out on the basis of national programmes received by the Commission in 
1993. Due to major differences in the level of detail and treatment of issues in these 
programmes, the initial evaluation was limited in scope. 
This report is the result of the second evaluation process which has been undertaken on the basis 
of National Communications/Programmes (2) which have been submitted under the Framework 
Convention on Climate Change and under the Monitoring Mechanism (apart from the Belgian 
programme which was submitted directly to the Monitoring Mechanism), and updates which 
have been officially communicated to the Commission before 1 July, 1995. The report is a first 
attempt to use the methodology for the evaluation of progress and content of national 
programmes, which has been developed and adopted by the Monitoring Mechanism 
Committee (3). This second evaluation report is therefore based on considerably improved 
information compared to the first evaluation report which was based on the existing national 
programmes which, at that time, were not complete, comparable or transparent due to the lack 
of detailed specification of common contents and structure (4). 
Following the Council Decision, six Committee Meetings under the Monitoring Mechanism have 
taken place. The summary records of these meetings include some updated information 
communicated by the Member States and this information has also been taken into account in 
the evaluation. 
The remainder of this project is set out in the following subsections. Section 2 reports on the 
C02 and other greenhouse gas emissions inventories and removals by sinks for EU-15. The 
1990 inventory is presented and historical trends, especially in energy related C02 emissions, 
are discussed. The greenhouse gas emissions inventory is only provisional at this point since 
the Member States have not yet provided their final emissions inventories. Section 3 provides 
an evaluation of progress towards the C02 stabilisation target. It reviews the content of the 
national programmes, the trajectories and the effect of measures. It focuses on the impact on 
C02 emission levels of national measures, as described in the National 
Communications/Programmes, rather than assessing the real effectiveness of these measures in 
reaching the Member States targets and objectives. Further details of the individual Member 
States' national programmes are given in the Annex. It compares the Member States own 
trajectories for the year 2000 with alternative trajectories prepared by the Commission services. 
Section 4 draws conclusions on the content and structure of the national programmes, the 
uncertainty in projections and the likely range of C02 emissions for the year 2000. 
ID 
Council Decision 93/389/EEC 
(2) 
In order to ensure consistency between the reporting requirements under the Framework convention on Climate Change 
(FCCC) and the EC Monitoring Mechanism, Member States may submit their National communications under the FCCC also to 
the Monitoring Mechanism as their National Programmes. 
(3) 
Fifth meeting of the Monitoring Mechanism committee, 18 May, 1995. 
C0M(94) 67 final, page 2. 
1 C^ 
1.2 THE COMMUNITY TARGET 
In 1993, the Council Decision for a monitoring mechanism of Community C02 and other 
greenhouse gas emissions was adopted 'in the framework of a Community strategy to limit C02 
emissions and to improve energy efficiency', to ensure that the Community is on course to fulfil 
both the stabilisation of C02 emissions in the Community as a whole by the year 2000 at 1990 
levels, and the commitments under the UN Framework Convention on Climate Change (5). Most, 
but not all, Member States have set national or EU C02 limitation targets or objectives which 
give an indication of the contribution they expect to be making to meeting the Community 
target. 
Greece, Ireland and Portugal have not adopted an official C02 target. Instead they have set out 
objectives in their National Communications/Programmes to limit the increase in C02 emissions 
to 15% (+/- 3%), 20% and 40% respectively. Finland has no base year for its target to 'stop the 
growth in energy related C02 emissions by the end of the 1990s', thus making the target unclear 
in numerical terms. Germany only has a target for 2005, a 25% reduction in emissions compared 
to 1990 levels. 
France and Spain have targets that allow some increase over current levels of emissions but 
which restrict the extent of that increase. France's position concerning the general commitment 
of maintaining the per-capita emissions of fossil carbon under 2 tonnes (which is 
equivalent to a 13% increase in emissions by 2000 over 1990 levels) is maintained (6) but it 
should not be considered as a specific target for the year 2000; instead, the preference is for 
commitments on policies and measures rather than to any quantified emissions limitations. 
According to new calculations which take into consideration the operational optimization 
of the nuclear power plants generating electricity, this first hypothesis of emissions 
increase has been revised downwards to + 7%. 
Denmark has a national target of a 20% reduction of its CO? emissions from energy and 
transport by the year 2005 compared to 1988. This target is formulated in terms of emissions 
corrected for net electricity trade, in both the base and the target year. Electricity trade fluctuates 
with water availability in the other Scandinavia countries, with exports in some years and 
imports in others. 
In 1990, with relatively large electricity imports emissions were at 10 % below the corrected 
emissions. Apart from its national C02 reduction target, Denmark has committed itself to 
achieve a 5% reductions in 2000 compared to 1990 as a contribution to the EU stabilization 
target. This commitment is also based on the corrected 1990 C02 emissions figures. 
The official Dutch target is a reduction of 3% in C02 emissions in 2000 compared with the 
1989/1990 levels. The Netherlands consider that teperature corrections is relevant for the 
development of adequate climate and energy policies. To enable policy development and 
evaluation , the Netherlands takes temperature variations into account by adjusting C02 
emissions. Therefore its 1990 base years has also been corrected for the weather conditions 
prevalent in 1990. The Netherlands strategy to reduce its C02 emissions by 3% therefore is 
built around this 1990 adjusted figure. 
Taking account of these targets and objectives, there is only a negligible gap between emissions 
targeted by the aggregate of Member State targets and the Community target. However, the 
assumptions made for the three countries that have neither a numerical target or an objective for 
the year 2000 (Finland, France and Germany) are critical for this outcome; their emissions 
represented 43% of total Community emissions in 1990. 
(5) 
Council Decision 93/389/EEC. 
(6) COM (94) 67 final Of 10.3.1994 p. 20 
2/3 
GREENHOUSE GAS INVENTORIES 
2.1 COMMUNLTY INVENTORIES 
Member State co2 CIL N,0 NO, CO i NMVOC C02 
Removals 
Austria 
Belgium 59200 
114500 603 
359 4 
22 222 
338 1692 
1219 445 NE 
NE 361 
Denmark 
Finland 52100 
53900 406 
252 11 
22 270 
295 770 
487 165 2600 
<31000 219 
France 
Germany 366500 
1013000 2896 
6218 176 
223 1722 
2944 10947 
10768 2424 32200 
20000 2978 
Greece 
Ireland 86100 
30720 936 
796 24 
42 543 
114 1143 
429 325 NE 
NE 197 
Italy 
Luxembourg 436300 
13300 3889 
24 116 
1 2034 
23 9258 
171 240] 36700 
NE 19 
Netherlands 
Portugal 151800 
42500 1067 
227 59 
11 575 
214 1029 
1083 459 100 
NE 199 
1120 
540 Spain 
Sweden 227300 
61300 2151 
329 94 
15 1189 
373 4725 
1612 23200 
34300 
UK 
EU-15 | 577000 I 4531 
\ 3285620 I 24671 108 j 2740 j 6682 • 2540 
928 ! 13546 ! 52006 ! 14397 6100 
Table 1 Emission Inventories for EU-15 for C02 and Other Greenhouse Gases 1990 (Gg) 
- Provisional Estimates: Estimates of Community greenhouse gas emissions are based on estimates of emissions 
submitted by the Member States. National estimates will be checked/confirmed with each country prior to finalising 
the totals for the EU. 
- The C02 removals are from Land use and Forestry. 
- Emissions from Final Non Energy Consumption (including feedstocks) have not been included 
in total emissions. Therefore, total emissions are underestimated in comparison with the IPCC 
methodology. Emissions from Final Non Energy Consumption (FNEC) are based on the total 
carbon contained in the products. The addition of total emissions and emissions from FNEC 
would therefore produce an overestimation compared to the IPCC methodology. 
- The UK and the Spanish emissions are based on recently updated national estimates adjusted 
to be in line with the IPCC guidelines. 
- The Spanish C02 emissions of 18700 G from agriculture and 2200 Gg from Waste are not 
included in the total national emissions since Spain has indicated that it considers all such 
emissions are of organic origin. 
- DK: Denmark has corrected its fuel combustion emissions for electricity imports/exports in 
1990. This correction (6300Gg of C02) has been excluded from the estimates presented in this 
report for reasons of consistency, no other Member States having made such a correction. 
- FR: C02 emissions of 8000 Gg from Waste are not included in the total national emissions 
since France has indicated that it considers all waste emissions are of organic origin. 
- IRL: In its national communication Ireland provided an estimate of NMVOC emissions from 
land use change and forestry of 17 Gg and was the only Member State to provide such an 
estimate. At the request of Ireland, this estimate has been included in the estimates presented 
in this report. 
- NL: In its National Communication the Netherlands provided estimates of C02 for actual 
emissions from feedstock (14800 Gg) and statistical differences (1000 Gg) which have not been 
included in the results presented in this report for reasons of consistency. Also it applied a 
correction for temperature influences which was not applied by other Member States and hence 
has also been ignored for reasons of consistency. 
Source: European Environmental Agency (EEA), June 1995. 
The most detailed and accurate emissions data are available for 1990 because it is the 
base year for the setting of policy targets within the EU and internationally. The Table 
below shows the emission inventories for the EU-15 for C02 and other greenhouse gases 
as also included in the EU Communication under the UN Framework Convention on 
Climate Change (7). 
The compilation of Community greenhouse gas inventories for 1990 provides a baseline 
against which the evolution of emissions can be measured. The Community inventory 
is based on the Member States' inventories which are submitted to the Commission 
under the Decision for a monitoring mechanism, using the same format as that required 
for reporting under the UN Framework Convention on Climate Change (FCCC). In the 
fifth Monitoring Committee meeting the Member States agreed to a systematic process 
of reviewing the data submitted to the Commission, described in the document 'Proposal 
for the Methodology for the Evaluation of Progress and for the Contents of National 
Programmes' (8). The change in emissions over time can then be measured by comparing 
the equivalent inventories for subsequent years with the 1990 baseline inventory. As the 
procedures for reviewing the data submitted by Member States have not yet been 
formalised, the inventories shown in the Table I are only provisional. 
This inventory data for 1990 is the most up to date and consistent Community data; it 
may differ from the 1990 data reported in some National Communications/Programmes, 
either because it is more recently estimated or because it has been produced using a 
different methodology. Since it provides a consistent basis for Member State 
inventories, it will be used as the baseline throughout the report. Complete inventories 
for other greenhouse gases were submitted for the year 1990 only. 
The EC greenhouse inventories are subject to review in the light of new scientific knowledge. The CO, inventory does not 
include sinks. 
(8) 
Fifth meeting of the Monitoring Mechanism Committee, 18 May, 1995. 
According to the Monitoring Mechanism methodology, the Member States should submit 
in July every year, provisional C02 inventories for the previous year and final 
inventories for the year previous to that. Community inventories are then compiled on 
the basis of the received data. The Member States are also encouraged to submit 
inventories of other greenhouse gases with their C02 inventories. 
In all Member States, C02 is the most important contributor to total anthropogenic 
greenhouse gas emissions. Data on the three main gases, C02, CH4 and N20, aggregated 
to show the climate change effect using IPCC direct global warming potentials 
(GWPs) (9), indicate that the contribution of C02 in the Community is approximately 
79%. Since the stabilisation target relates only to C02, the evaluation of progress in this 
report concentrates on that gas and not on other greenhouse gases. 
Total anthropogenic C02 emissions in the Community amounted to an estimated 
3,329,750 Gg in 1990 which is approximately 13% of total global anthropogenic 
emissions (10). Since there is no agreed C02 inventory for the EU-15 for 1993, it is not 
possible to make a comparison of review year data (1993) with base year data (1990), 
as is required by the Monitoring Mechanism methodology. 
2.1.1 Historical Trends in Energy Related C02 Emissions 
Within the Community C02 emissions arise largely (95%) from the combustion of fossil 
fuels used as energy sources for power generation, industry, transport and households. 
Since the contribution of energy related C02 emissions to total C02 emissions is so 
significant, it is possible to get an indication of the historical C02 emission trends by 
studying energy related emissions only. 
Between 1990 and 19.93 (the review year in the second evaluation process) energy 
related C02 emissions in the Community as a whole fell by 2.2% (11) and C02 intensity 
both on a per capita and per GDP basis has fallen (12). It is important to note, however, 
that, as opposed to Member State emission inventories and the Community C02 
inventory, the C02 estimates on which these figures are based have been calculated 
using harmonised emission factors (13). The absolute emission figures by country will 
therefore not correspond to the EU inventory figures. However, the 2.2% reduction is 
indicative of the evolution of C02 emissions over the review period. 
Energy related C02 emissions have fallen only in three out of the fifteen Member States 
(Austria, Germany, and the UK). Developments in Germany are of particular 
importance to changes in emission levels in the Community, contributing 30% of 
(9) 
Radiative Forcing of Climate Change: the 1994 Report of the Scientific Assessment Working croup of IPCC. Global Warming 
Potentials (CWPs) of 24.5 and 320 tonnes of CO, equivalent for CH4 and N20 respectively, based on IPCC Direct GWPs on a 100 
year time horizon. 
(10) 
Radiative Forcing of Climate Change: the 1994 Report of the Scientific Assessment Working Group of IPCC. 
in) 
Eurostat, May 1995. Energy related emission data, based on harmonised emission factors. 
(12) 
GDP and population figures from Eurostat, June 1995. 
(13) 
The use of emission factors may vary between countries simply because the chemical composition of the fuels actually are 
different in different countries. However, differences may also arise because the underlying assumptions about the 
conversion of carbon to co2 differ, i.e. assumptions regarding complete and incomplete combustion. Some international 
organisations use harmonised emission factors for all countries, a method which inevitably will mask differences in chemical 
fuel composition which often actually exist across the Member States. 
Community emissions in 1990. As a result of reunification in 1990 there has been 
considerable economic restructuring in the former GDR and a significant switch in fuel 
use away from brown coal. In the new Lander, C02 emissions decreased by 50% 
between 1987 and 1993 while emissions increased in former West Germany by 2% over 
the same period. It is doubtful if the total fall in emissions in the former GDR can be 
sustained once the economy is consolidated in that region. Emissions are likely to grow 
with development and economic growth although ongoing investments in very energy 
efficient technologies can maintain some of the emission reduction which has been 
realised between 1990 and 1994. 
While the period between 1990 and 1993 was characterised by low economic growth in 
the Community (annual percentage change of 0.7% (14)), 1994 was a year of recovery 
which is expected to be consolidated over the next few years. Projections indicate that 
annual economic growth between 1995 and 2000 could be 3.3% (15). Part of the 
émission decrease over the review period must be attributed to low economic growth in 
the Community. Apart from economic growth projections, other factors indicate that the 
C02 trend is likely to turn upwards between 1995 and 2000 and continue to rise 
thereafter. Forecasts from the International Energy Agency (IEA) which are based on 
country energy forecasts for EU-15, show an increase in energy related C02 emissions 
between 1990 and 2000 of 6%, and for the eight EU countries that have submitted 
forecasts post-2000, a 7% increase by 2010 (16). 
Whereas energy related emissions in most sectors have levelled off during the review 
period, or substantially fallen, as is the case in industry largely due to reduced 
production levels, they are still rising in the transport sector (7% increase 1990-1993). 
Transport demand and traffic in the Community are expected to increase significantly 
in the future, especially following the completion of the internal market. Since 1970 
annual growth in inland transport has averaged 3.1% for passengers and 2.3% for 
goods (17). Emissions from this growth in traffic volume will only be partially offset by 
improvements in efficiency but emission levels overall are projected to increase. 
Both in 1990 and in 1993, eight of the Member States generated more than 20% of their 
electricity from carbon-free sources, nuclear or hydro. However, in three of the eight 
countries that have nuclear power plants, the contribution (% of total) of nuclear in 
power generation has decreased as has the contribution (% of total) of hydro power in 
eight of the Member States. 
(14) 
European Commission, Medium Term Projections 1995-2000, June 1995. 
European Commission, Medium Term Projections 1995-2000, June 1995. The OECD Economic Outlook (57), June 1995 also 
projects a consolidation of the economic recovery in Europe over the next few years. 
(16) 
IEA, projections based on country energy forecasts, 1994. 
(17) 
Commission of the European communities (1993). Towards Sustainability. A European community programme of policy 
and action in relation to the environment and sustainable development. 
2.2 REMOVAL BY SINKS 
Greenhouse gas sequestration is an option applicable mainly for C02 since it is the only 
greenhouse gas which has large natural sinks, in the oceans and in biomass. Other 
greenhouse gases are mostly broken down in the atmosphere so the absorption option 
is not relevant to them. The removal of C02 by sinks can make an additional 
contribution to the overall reduction of C02 in the atmosphere, particularly in those 
Member States that have a significant potential to increase forest areas. The national 
programmes contain only very limited information on the actual removal of C02 by 
sinks and the policies and measures which Member States have taken to increase the 
sequestration of C02 emissions. 
2.3 CONCLUSIONS 
Based on Member States' own targets and objectives, five countries expect to reduce 
C02 emissions by the year 2000, while four countries aim at stabilising emissions and 
six countries plan to increase C02 emissions by the year 2000. 
The 1990 inventory of C02 and other greenhouse gas emissions has been prepared, 
based on the national inventories and other up-to-date information supplied by the 
Member States to the Commission. Since this information is more recent than that used 
in some Member States national programmes, and also that some differences in 
inventory methodologies exist, the EU inventory differs from some of the Member States 
national programmes. The 1990 EU inventory forms the baseline for evaluating progress 
towards the C02 stabilisation target. The compilation of an EU inventory for subsequent 
years, especially the 1993 review year, has not been possible due to the inadequate 
information submitted by Member States. 
EVALUATION OF PROGRESS TOWARDS THE TARGET 
3.1 CONTENT OF NA TIONAL PROGRAMMES 
This report takes into account Member States' National Communications/Programmes 
and their updates received officially by the Commission by 30 June 1995. In accordance 
with the Council Decision for the Monitoring Mechanism for C02 and other greenhouse 
gases, all Member States have submitted national programmes (for all countries but 
Belgium, the national programme is the Communication under the Framework 
Convention for Climate Change (18) ), to the Commission, containing 1990 emission 
inventories, details of national policies and measures, measures for the implementation 
of Community legislation and policies, and trajectories of future emissions. 
Considerable progress has been made since the submission of the first, very 
heterogeneous national programmes (19) in 1993. Nevertheless, the second evaluation of 
progress towards the C02 stabilisation target is complex due to the fact that the 
information contained in the National Communications/Programmes still is either not 
comparable between the Member States or incomplete, even though Member States have 
made considerable efforts to satisfy the requested reporting requirements. The main 
factors that make an evaluation problematic are: 
• The EU inventory is based on the latest information, and not all Member States have 
provided updates to their national programmes to recalculate the measurement and 
targets in relation to this inventory. Therefore there is some inconsistency between 
the inventories in the.Member States national programmes and the EU inventory. 
• Insufficient information about measures, to give an accurate picture of the state of 
implementation, progress and availability of funding for these measures, make it 
difficult to evaluate the effect that the measures will have on C02 emissions before 
2000. 
• Not all countries adequately distinguish between policies and measures put in place 
prior to the base year of their climate policy and measures which are formally part 
of their programme. 
• C02 trajectories for the year 2000, developed through different models and based on 
different assumptions, make it difficult to compile a Community trajectory for 2000 
based on the sum total of the Member State trajectories. The total lack of 
trajectories, either with or without measures or both, for certain Member States 
further complicate the process. 
(18) 
For 1995 it was agreed by the Monitoring Mechanism committee that the EC would accept the National communications 
as the national programmes. All Member states have ratified the convention except Belgium, which is in the process of doing 
so. For the next evaluation, updates to the national programmes are expected. 
(19) 
The agreed format for content and structure of national programmes, and the reporting guidelines under the Framework 
Convention, were not available early enough to ensure consistency for the first evaluation. 
3.2 CO2 LIMITA TION STRA TEGIES IN THE COMMUNITY 
C02 emission strategies exist at both the Community and the Member State level. The 
Community strategy was adopted by the Council in 1991 (20). It includes: 
non-fiscal measures in the framework of Community programmes (SAVE, 
ALTENER, JOULE, THERMIE); 
• a proposal for a combined C02/energy tax (now a revised proposal for common 
guidelines for a combined C02/energy tax); 
a Monitoring Mechanism. 
The Community strategy will only be effective to the extent that the measures which 
have been adopted at the Community level, actually are implemented in the Member 
States. Most Member States have included the Community measures in their national 
C02 strategies. In particular, energy efficiency labelling is considered to have great 
potential, and five countries have indicated that a carbon/energy tax at Community level 
is necessary to achieve their national targets (Belgium, Denmark, Germany, Italy, 
Netherlands). 
Only Denmark, Finland, the Netherlands and Sweden have introduced C02 taxes to date 
but most countries apply VAT on energy at various rates and many countries have 
introduced taxes on fuels. The Nordic countries which have C02 taxes in place would 
like to increase these taxes further to fully exploit the potential of the measure, but they 
are reluctant to do so for reasons of competitiveness, unless a similar tax is introduced 
at the Community level. 
France has indicated that a C02 taxation at the EU level is necessary in order to limit 
its C02 emissions at their level indicated in their National Communication. 
Belgium and the Netherlands have declared that unless there is progress on the EU 
C02/energy tax proposal, they will introduce a tax unilaterally in 1995. Similarly, the 
new government in Austria says that it is considering introducing a C02 tax in 1996 or 
at the latest in 1998 (21). If the revised Commission proposal for guidelines for the 
introduction of a combined C02/energy is adopted by the Council, the introduction of 
a tax would be done within a common framework by the Member States. 
At the national level, all Member States have developed and adopted C02 limitation 
strategies which are described in the National Communications/Programmes. In general, 
there are three main approaches to the limitation of C02 emissions: (examples of these 
approaches in various Member States may be seen in the Annex). 
• Efficiency improvements which result in a reduction in the level of inputs to achieve 
a given level of output. Generally for C02 emissions we are concerned with levels 
(20) 
SECOD1744 final, October 1991. 
(21) 
Fifth meeting of the Monitoring Mechanism Committee, 18 May 1995. 
10 
of energy efficiency. Energy efficiencies can be brought about through technological 
advances or improved management practices, or changes at the energy system level 
(eg reducing the total emissions from power and heat production through combined 
production of heat and power). 
• Consumption changes including conservation measures which result in an overall 
reduction in consumption, for example through cutting out unnecessary uses of energy 
and modal shifts especially in transport involving changes from one energy intensive 
form (eg private motor cars) to a less energy intensive mode (public transport). 
• Fuel switching from fuels with high to those with low or zero carbon coefficients, for 
example shifting from coal to gas for power generation, or to renewables. 
An additional measure is the sequestration Sequestration of C02 by soils and vegetation 
which similarly reduces the level of C02 in the atmosphere and, which has a similar 
effect to reducing emissions. 
There are a range of different measures that are used in the Member States to implement 
C02 limitation strategies to achieve the effects described above: 
• Economic instruments such as C02 or energy taxes are used in order to provide 
incentives to improve efficiency in the use of energy, changes in consumption or to 
encourage switching to less carbon intensive fuels - they are also used to encourage 
expansion of forested areas and thus increases in rates of C02 sequestration, eg via 
planting subsidies. 
• Regulations introducing energy efficiency standards or restricting uses of particular 
fuels encourage energy efficiency improvements or fuel switching. 
• Information & education programmes are used to encourage energy efficiency 
improvements in industry and energy conservation by firms and householders - these 
schemes include energy labelling and advertising campaigns. 
• Government direct action is significant where it is a major user of energy - this might 
include improvements in energy efficiency in buildings, investment in new electricity 
generation capacity or increased afforestation of state-owned land. Government action 
to de-regulate energy markets may create incentives for improvement in the thermal 
efficiency of generating plants, reduced electrical losses from transmission and 
distribution systems and can result in switching towards fuels with lower carbon 
content. 
• Research & development mostly has long term impacts, eg through encouraging the 
development of energy efficient and renewable energy technologies or on methods 
for C02 disposal. 
11 
3.3 TRAJECTORIES AND EFFECTS OF MEASURES 
3.3.1 The Effect of Policy Measures 
The Member States have introduced or are in the process of implementing a broad range 
of policy measures in order to tackle C02 emissions. The most wide spread measures 
are aimed at energy conservation and energy efficiency measures in end-use. A number 
of countries have programmes to encourage fuel switching, particularly via government 
action in the energy sector. The national C02 strategies are summarised in the country 
summary pages in the Annex. 
Member States have the option of introducing different types of measures, the choice 
of which has a significant influence on the degree of uncertainty related to the 
effectiveness of the measures. The following aspects influence the effect of measures: 
Compulsory versus voluntary measures 
Compulsory measures or 'hard measures', such as taxes, regulations and standards that 
must be complied with, and which have a fixed date of implementation, tend to 
generate more secure results than voluntary measures or other 'soft measures' such as 
information and education. Compulsory measures are mostly introduced in the 
household and commercial sectors in the form of efficiency standards and regulations. 
These measures can be very effective even in a reasonably short period of time. 
For the four countries that have introduced C02 taxes, carbon and energy taxation are 
a fundamental part of these countries' C02 strategies. These taxes tend to be cross-
sectoral. For reasons of competitivity, the C02 tax on industry is lower than for other 
sectors in Denmark and Sweden (where power generation is totally exempt from the 
tax). In Denmark and Finland, rates for all sectors are significantly lower than they 
would be had the tax been introduced in all Member States. In an indirect way the 
C02 tax is an important part of the C02 strategies of Belgium, Germany, Italy and 
the Netherlands since all of these countries have stated that the tax is necessary for 
them to reach their respective targets. France is also convinced that the C02 taxation 
is an important part of its C02 strategy and in terms of excise taxes it has increased 
the latter on diesel fuel by 20% in real terms between 1990 and 1995. 
Voluntary measures in some form are included in the C02 strategy of several Member 
States, and mainly introduced in the industry sector with the aim of promoting energy 
conservation. Voluntary agreements, supported by a system of environmental permits, 
are at the core of the Dutch C02 strategy. The efficiency of such measures depend 
on the size and structure of the industrial sector, the efficiency of monitoring and 
enforcement and on the system of cooperation between the social partners. The 
results, which can be very efficient, will therefore vary from country to country. 
Other 'soft measures' include information and training but in most strategies this is 
viewed as a support measure for the enhancement of energy conservation in 
particular, rather than a core measure. 
Funding Status 
12 
Measures that have secure funding, for example through the fixed allocation of tax 
revenues or EU grants, will be more secure than measures that depend on annual 
decisions regarding continued funding, as do for example subsidies and investments, 
both public and private. Subsidies are included in most C02 strategies and are often 
given for the promotion of renewable energy sources, for the promotion of public 
transport and for demand-side-management (DSM). 
Funding is an important factor influencing the outcome of all C02 strategies, 
particularly in times of recession and unemployment. The UK expects emissions 
reductions as a result of the establishment of an Energy Saving Trust. Due to 
changes in the anticipated levels of funding the contribution is now expected to be 
lower (at a minimum of 0.3 MtC) than originally estimated - although further 
schemes are being developed by the Trust which will contribute further savings. 
• Long term measures 
Long term measures, such as R&D measures or major investments in infrastructure, 
are uncertain by nature, since they span over a longer time frame. Funding, political 
backing or other important determinants for the implementation of these measures 
could change with, for example, fluctuations in economic growth. The measures in 
the French national C02 strategy are mostly expected to have a long term impact, 
beyond the year 2000. The measures included in the strategies of the southern 
Member States tend to focus on infrastructure investments which are also for the 
longer term. Often the measures in the transport sector are for the longer term; eg 
the development of public transport or energy efficient vehicles and modal shift, are 
medium to long term measures. 
The likelihood of achieving the Community stabilisation target for C02 emissions is 
dependent on a number of factors, but the effect of policy measures is of key 
importance, illustrated by the magnitude of difference between the with and without 
measures scenarios (see A nnex A, Table A 2). Due to the uncertainty related to the 
implementation and actual effect of measures, the with measure scenario could be 
viewed as an estimated reduction potential, although the real outcome in 2000 could be 
very different. It is therefore very important to be able to estimate the effect of 
measures, but very difficult to do so on the basis of the National 
Communications/Programmes since the information provided in them is generally 
inadequate. As a rule, the National Communications/Programmes are unclear regarding 
the following points. 
• The status of policy measures, whether adopted, in the process of adoption or merely 
options being considered. Even where this is indicated it is difficult to discern 
whether implementation has begun, the level of effort related to the implementation 
of the measure, and whether funding is secured for the future. 
• Whether or not the measure is introduced as part of the national climate change 
policy or for some other policy reason. 
• The effects of a measure on levels of emissions measured in C02 emission reduction, 
consistent with the difference between the with and without measures scenarios. 
13 
Even where this information is provided it would be useful to have progress 
indicators for the implementation of the measures so as to be able to evaluate the 
likelihood that the full effect of the measure will be realised by the year 2000. The 
effects of measures are only partially comparable across countries since they have 
been estimated using different models and assumptions. 
• The trajectories do not give projected C02 emissions with and without measures for 
every year between 1990 and 2000, against which the effect of measures to date 
could be evaluated. 
3.3.2 The Effect of Removal by Sinks 
The enhancement of removal of C02 by sinks, generally through the encouragement of 
forestry, is not counted as part of achieving the Community C02 target, which is 
currently based only on emissions. One problem with including the removal by sinks 
in the achievement of targets is that trees can remove carbon from the atmosphere for 
long periods, particularly if the wood is harvested and used for construction materials 
or other long term purposes, but not permanently. Afforestation does not halt the gross 
growth in emissions or affect the main cause of rising C02 emissions, namely the 
combustion of fossil fuels. This may be an issue particularly for countries where the 
increase in sinks would otherwise mask an increase in emission levels over time. 
It is estimated that, within the Community, there may be a total of 350,000 ha of new 
planting over the period 1990-2000 including 100,000 ha on former agricultural land as 
a result of reforms to the Common Agricultural Policy (CAP) and 250,000 ha in 
response to Member State policies and commercial incentives (22). 
Member States have, in most cases, included measures for sink enhancement in the 
national C02 strategies. Four countries have no measures for the enhancement of sinks 
and one country's measures are only in the conceptual phase. The measures which are 
being implemented are very similar in all the countries, including for the most part 
afforestation, forest maintenance and forest management and promotion of long-lived 
wood products. 
3.3.3 Member State Trajectories for the Year 2000 
In order to provide an up to date picture of the likely achievement of the Community 
stabilisation target, Table AI (in the Annex) provides an aggregation of country 
trajectories of emissions for 2000. These trajectories are based on Member State 
submissions in National Communications/Programmes, and updates which have been 
officially communicated to the Commission. The trajectories are based on the 
assumption that there is no Community C02/energy tax in the countries that have not 
yet introduced such a tax. 
(22) 
Environmental Resources Management (1994) Forests as C02 sinks Final Report to the European Commission DCXI/B/4. 
14 
The trajectories and projections for 2000 have been adjusted to be consistent with the 
same 1990 baseline, the EU C02 inventory for 1990 (see section 2.1). Where the 
Member States have provided both a with and without measure scenario, the effect of 
measures has been calculated as the difference between the two. In the cases where 
only one projection has been given by the Member States (generally with measures), the 
other scenario is derived on the basis of information in the National Communication on 
the effects of measures, and using a consistent set of assumptions regarding economic 
growth rates and fuel prices. However, Table Al does not show the 'without measures' 
trajectories since they were not submitted by all countries. 
By adding up the individual Member State trajectories and projections, we can estimate 
Community C02 emissions in 2000. It should be noted, however, that this method of 
compiling a Community trajectory only can give indicative results, since the broad range 
of models and assumptions that have been used by the Member States introduces a 
certain amount of inconsistency between their trajectories. In addition, some Member 
States have made trajectories of projections for all C02 emissions whereas others only 
for energy related emissions. The figures in the table do not take account of these 
differences. Finally, in virtually all cases, the base year data which have been used in 
the trajectories and projections do not correspond with the EU C02 inventory. By using 
the magnitudes of change rather than absolute levels, a link can be established between 
the trajectories and the EU inventory, but this method further results in the trajectories 
in Table 3 differing from those reported by the Member States. 
Bearing the above limitations in mind, this analysis indicates that the Community may 
stabilise emissions at 1990 levels by the year 2000 if the Member States achieve their 
trajectories. Germany continues to be a main contributor to C02 emissions, but its share 
would fall from 30% in 1990 to 24% in 2000. Due to the exceptional situation in 
Germany as a result of unification in 1990, Germany will likely make a significant 
contribution to Community C02 emission reductions. However, it is doubtful whether 
this reduction is permanent if economic growth in the new Lander is faster than it has 
been since 1990. In 1994, GDP expansion was estimated to be 9% in the Eastern 
Lander, and it is expected that the former GDR will continue to be the fastest growing 
region in Europe over the next couple of years (23). Projections for Germany will 
therefore be particularly sensitive to assumptions about GDP growth; the assumption 
underlying the minus 13% scenario is not specified. 
The trajectories and projections are in general sensitive to assumptions both about GDP 
growth and about international fuel prices. A major source of uncertainty pertaining to 
the results described in the table above, therefore, relates to the fact that not all countries 
have specified the assumptions that they have used. Where assumptions are transparent, 
they tend to differ from country to country (eg Italy assumed that oil prices in 2000 will 
be $15/bbl while Sweden assumed that the same international prices will be $28/bbl). 
Some such differences may reflect real differences in costs of delivered fuel, but as 
regards, for example, international fuel prices, assumptions across Member States should 
have an underlying consistency. 
(23) 
OECD Economic Outlook (57), June 1995. 
15 
Another source of uncertainty is the estimated implementation of measures, both as 
regards the technical calculation of the effect of measures, and the level of actual 
implementation. In the table above the effect of measures has been assumed to be the 
difference between the with and the without measures scenario. Not all Member States 
have provided a without measures scenario, but even where it has been submitted, it has 
a different meaning for different Member States. Most countries have, in some way or 
other, included measures in the without measures scenario, although some leave them 
undefined, for example only describing them as 'optimising the use of energy' as in the 
case of Austria, while others explicitly state that the measures implemented up until a 
specific date have been included in the without measures scenario, as in the case of the 
Netherlands. 
If the with and without measures scenarios have been generated at different times, their 
underlying external assumptions may differ. Such differences will then be masked as 
being part of the effect of the measures, particularly when the underlying assumptions 
are not transparent. 
In the with measures scenario, Member States have used widely different models and 
methods of estimating the impact that measures would have. Regardless of method 
used, the estimation is complicated by the fact that, for example, some measures may 
only have an effect if implemented jointly while the effect of other measures may not 
be fully additive because their reduction potential may overlap. The way in which 
countries incorporate, into their macro-economic models, the effect of measures which 
have been calculated at the micro level, also varies greatly across Member States. 
Only four Member States have clearly quantified each measure which is included in the 
with measures scenario (Belgium, Greece, Sweden and UK). In other cases, where the 
sum of the quantified measures exceeds the difference between the with and without 
scenarios, the assumption has been made that the sum of quantified measures constitutes 
a potential rather than an actually achievable impact (eg for Finland 16000-18000 
GgC02 is assumed to be the potential but only 9000 GgC02 is taken to be achievable 
effect of the measures, since this is the difference between the two scenarios). 
Germany has listed 109 measures but none of them has been quantified. The German 
estimate is further complicated by the fact that no projections have been provided at all 
for 2000. The 13% reduction figure is a rough estimate which has been communicated 
to the Commission (24) but none of the underlying assumptions or measures which are 
taken account of are known (an emission reduction range of 13%-16% was 
communicated to the Commission; the lower estimate has been assumed in Table 3). 
Related to the calculation of the effect of measures is the uncertainty regarding the 
implementation of measures discussed in the section above. All countries have measures 
that remain to be implemented and for some Member States such measures constitute 
the major part of the C02 strategy (eg Belgium). If implementation is not started soon, 
the measures cannot be expected to have an effect by 2000. 
(24) 
Oral communication, Monitoring Mechanism Committee meeting, February 14,1995. 
16 
Given that four countries, namely France, Germany, Italy and the UK accounted for 72% 
of Community C02 emissions in 1990, minimising uncertainties associated with the 
implementation of their respective measures is of particular importance. The French 
measures are mainly for the long term beyond 2000 (25). According to the German 
Communication, 88 measures are under implementation but there is very little indication 
of what that means in terms of level of effort, duration, political commitment, 
availability of funding etc and as noted above, the impact of the measures has not been 
quantified. The Italian plan shows an unusually large effect of measures although it is 
not indicated where this reduction would come from. The stage of implementation of 
the measures is very unclear and none of the measures have been separately quantified. 
In the UK, following changes in the anticipated level of funding, the contribution of the 
Energy Saving Trust is now expected to be lower than originally estimated. 
Greece, Ireland, Portugal and Spain all have 'objectives' that take account of their 
expected higher economic growth. These objectives correspond to their respective 
projections. Greece revised its 'realistic objective' downwards from a 25% increase to 
15% +/- 3% increase (26). This is more related to revised expectations about economic 
growth than to a higher than expected effect of measures. Emissions in these countries 
are likely to be more linked to economic growth in the years up to 2000 than to the 
implementation of the measures in their national C02 strategies. It is therefore likely 
that if economic growth proceeds as forecasted in these countries, emissions will follow. 
The measures in these plans are not fully elaborated (with the exception of Greece), 
highly dependent on the availability of funding and therefore unlikely to counteract the 
increase in emissions. 
Several of the countries that use nuclear power are finding it increasingly difficult to 
acquire the public's consent to build new power plants (eg in Finland Parliament rejected 
the application to build a fifth nuclear power plant. 
In France four 1450 MW PWR units are now under construction and expected to be 
commissionned before the year 2000. Having regard to current forecasts of electricity 
consumption, the improved availability of French nuclear plants and the expected extent 
of its exports, it is not expected that further nuclear reactors will be ordered before the 
year 2000. However, if the level of 70 ECU a tonne of carbon not emitted were to be 
regarded as necessary to stabilise emissions from the European Union, the French 
nuclear investment policy would be revised. 
Sweden has made its projection on the assumption that the planned phase-out of nuclear 
power is not initiated before 2000. Even if that is the case, new energy demand must 
be met with power generation from fossil fuels, especially since there is, in principle, 
a ban on expanding hydro power. Once the phase-out is begun emissions from the 
power generation sector are likely to increase significantly. 
(25) 
summary record of the Committee meeting of the Monitoring Mechanism, 19 October, 1994. 
(26' Summary record of the Committee Meeting of the Monitoring Mechanism, February 14,1995. 
17 
3.3.4 Alternative Trajectories for 2000 
Since there is considerable uncertainty related to the trajectories and projections 
discussed above, it is useful to compare them to alternative projections; a modified 
projection based on the Member State trajectories but using a few common assumptions, 
especially a sensitivity analysis on growth rates, and a further Commission projection 
based on new energy scenarios. 
In the 'modified projection', country GDP growth rates (in place of those given by the 
Member States) have been used that are consistent with the projected Community growth 
rate and fuel import prices, (particularly for crude oil) pertaining to the EU (27). For the 
years 1990-1993, estimated actual C02 emission growth from energy only has been 
used (28). Thereafter, emissions are estimated forecasted based on OECD GDP 
projections for 1993-1995, and Commission Services' projections for 1995-2000 (29). 
The 'Commission projection' is based on a provisional result from a recently updated 
energy scenario using the Commission's energy models (Conventional Wisdom scenario 
2020). It shows an increase in emissions from energy consumption of approximately 
5%. 
The Member States are committed to their trajectories shown in Table A 2 (in the A nnex) 
column (a). However, the alternative scenarios shown in columns (b) and (c) highlight 
the uncertainty present in any future projections. 
As all projections, the two alternatives which are presented in Table A 2 have 
shortcomings. The different results in these trajectories show the importance of the 
underlying assumptions. In the Member State trajectories the assumptions about GDP 
tend to be lower and assumptions about fuel prices higher than the ones used in the 
modified trajectory. This partially explains why the Member State trajectory for EU-15 
shows an emission decrease while the other two projections show an increase. Another 
reason may be that the Member State trajectories may assume successful implementation 
of all measures while the alternative trajectories may allow for some slippage in 
implementation. As regards these underlying assumptions, it is likely that the modified 
and the Commission projections are more consistent since they are based on common 
external assumptions. The methodological problems discussed in the section above are 
identical for the Member State and the modified trajectories as is the uncertainty 
pertaining to the implementation of measures. The 'bottom-up' approach used in the 
Member State trajectories may be contrasted with the Commission trajectory which is 
based on 'top down' analysis. 
Based on the projections above and the uncertainty related to the implementation of 
measures, the most likely development is an increase by the year 2000 in the range of 
0-5%. This range also takes account of uncertainty in fuel prices and GDP growth rates. 
(27) 
Assumptions regarding GDP growth from Commission Services (DCll), 'Medium Term Projections 1995-2000", June 1995. GDP 
figures 1992-1995 from OECD Economic outlook (57), June 1995. Import prices for oil taken from OECD Green model (June 
1995), which projects a change of S4979-S4052 per terrajoule from 1985-2000 for the EU. Energy price assumptions have also 
been taken from "A View to the Future', September 1992. 
(28) 
Eurostat, June 1995. Harmonised emission factors. 
(29) 
The 2000 emission data have been projected using a "change index" constructed on the basis of the OECD/Commission GDP 
growth rates and fuel prices taken from the OECD Green model, the GDP growth rates included in the National 
Communications, and assumptions about income and price elasticities. 
18 ( vc\ 
CONCLUSIONS 
There has been considerable improvement in the quality of reporting in the National 
Communications/Programmes since the first National Programmes were submitted for 
evaluation in 1993. However, the information provided in them is still insufficient, in 
terms of specific details, to evaluate progress towards the Community stabilisation target 
in a satisfactory way. Overall there is still considerable uncertainty regarding the 
expected outcome in the year 2000. Due to lack of key information, it has not been 
possible to fully apply the methodology adopted by the Monitoring Mechanism 
Committee (30). Notably, the following important compromises have been made for lack 
of information and lead to additional uncertainty about the expected outcome for 2000: 
• Since there is no Community C02 inventory available for the review year 1993, it has 
not been possible to review the trend in emissions between the base year 1990 and 
the review year. 
• The compilation of a Community trajectory for 2000, which should be based on the 
trajectories supplied by Member States, was not possible due to difference in 
methodology and assumptions used by the Member States. Two alternative 
trajectories have therefore been presented. One is a modified trajectory with 
consistent growth and fuel price assumptions, the other is based on the Commission's 
energy scenarios for 2020. Both of these alternative scenarios estimate higher C02 
emission for 2000 than the Member States' own trajectories. 
• There is insufficient information about the implementation of measures. This is a 
crucial element in the assessment of progress. The reliability of the trajectory results 
are particularly hampered by the fact that the reporting of implementation of measures 
in four of the largest contributors to C02 emissions, Germany, France, Italy and the 
UK (representing 72% of emissions in 1990), is insufficient. In general, it is 
impossible to make an assessment about the effectiveness of implementation of 
measures based on the national programmes since adequate information is not 
provided. 
These are shortcomings in this evaluation report that should be addressed in the third 
evaluation due to take place in 1996. More consistent and transparent data are required 
to allow better presentation and evaluation in subsequent reports; the documents (31) 
agreed at the Fifth meeting of Monitoring Mechanism Committee on 18 May, will help 
provide such data. Furthermore, amongst other possibilities, it has been suggested that 
a workshop might be arranged in which the development of trajectories could be 
discussed. The Monitoring Mechanism Committee also foresees a working group to 
assist in the process. 
(50) 
Fifth Monitoring Committee meeting, May 18,1995. 
(31) 
Fifth Monitoring Committee meeting, May 18,1995: "Proposal for the Contents and Format of Annual Inventories' and 
•Proposal for the Methodology for the Evaluation of Progress and for the contents of National Programmes". 
20 
According to the results of this evaluation process, it cannot be excluded that 
Community emissions will increase within the range of 0-5% by 2000 over 1990 levels. 
The lower end of this range is based on the assumption that the maximum potential of 
the estimated effect of measures as reported in the 'with measures trajectories' of the 
Member States, is actually realised. Since current emissions are below 1990 levels, even 
stabilisation by 2000 implies that emissions will be growing between now and then. If 
energy prices remain low and GDP growth is faster than expected the increase could be 
at or above the top of the range. Such an increase of 5 % or more would be a serious 
departure from the agreed stabilisation commitment. 
As mentioned above there is also uncertainty linked to the implementation of measures 
and many will only have an impact after 2000. Five countries have said that they can 
only meet their targets if a C02/energy tax is implemented at the Community level. If 
the full potential is not realised, C02 emissions could increase more, unless additional 
measures are implemented. 
This evaluation takes account of the emissions and national programmes of 15 Member 
States, and the picture has therefore changed since the previous evaluation which only 
included 12. Subsequent evaluations are expected to be based on improved information 
by including recent updates by Member States of their national programmes and a 
reporting format more closely aligned to the adopted methodology. 
It appears therefore that, at this stage, the Commission is not in a position to claim that 
the adopted policies will be sufficient to meet the agreed targets and certainly not to 
ensure reductions in C02 emissions after the year 2000. 
The Council of 22/23 June 1995 invited the Commission to modify the Monitoring 
Mechanism decision of 1993 to extend the monitoring of greenhouse gases beyond the 
year 2000. This is important since it is likely that the Community emissions will be 
increasing after 2000 event though measures implemented will have a continuing effect. 
IEA energy projections, recalculated as C02 projections, show that for the eight EU 
countries that have submitted post-2000 projections, energy related emissions in 2010 
could be 7% higher than in 1990 (32). Taking a post-2000 perspective therefore also 
becomes increasingly important for subsequent evaluations. 
(32) IEA Energy related C02 projections, June 1995. The eight countries are: Belgium, Finland, France, Germany, Ireland, 
tuxembourg, Netherlands and the UK. 
21 
Annex A 
Tables Showing C02 
Inventories, Trajectories 
and Effects of Measures for 
the 15 Member States 
22-
Table A1 Member State Trajectories and Projections and Effect of Measures (S> 1990-2000(CgCO2)-Adjusted on a Common 1990 baseline (GgC02) 
Member State (a) j 
C02 Inventory 
1990(1) I (b) 
Change 1990/2000 
I Austria 59200 ! (c) 
% change 
1990/2000 (d) 
Trajectory 2000 
(With Measures) ° (e) 
Effect of Measures Comments'3 
380 0.6 59580 5520 j STAB scenario is 'with measure' scenario. STAB aims at stabilising 
i emissions at 1990 levels by 2005 (reduction of 8800 GgC02 over 1ER 
! reference scenario for 2005). Effect of measures interpolated for 2000. 
Belgium 
Denmark 
Finland 114500 •1300 -1.1 113200 13630 Projection is temperature corrected. Bureau de Plan scenario without a 
CO, tax is 'with measure' scenario. 
52100 -6200 -11.9 45900 13500 | Energy 2000 follow-up trajectory 1990/2000 is 'with measure' scenario. 
| Aim is to achieve 20% reduction by 2005 compared to 1988 levels. 
53900 16000 29.7 69900 9000 j Energy related emissions only. Assumption that all imported electricity 
| produced domestically in future (see country summary). 
France 366500 31840 398340 73200 | Scenario 1 from note to Monitoring Mechanism Committee is 'with 
; measure' scenario, including sinks. 
Germany 1013000 -131560 -13.0 881440 144330 j 'Without measure' scenario is derived based on assumptions of consistent 
j set of fuel prices and GDP growth rate. 'With measure' scenario for 
I 2000 is 13% reduction over 1990 levels, as communicated to 
I Commission in Monitoring Mechanism Committee meeting in February 
! 1995. 
LP Greece 86100 12320 14.3 98420 9590 'With measure' scenario is 'most realistic objective' of 15% increase by 
2000 over 1990 levels. 
Ireland 30720 6300 20.5 37020 1390 ! 'Without measure'scenario is derived based on assumptions of 
j consistent set of fuel prices and GDP growth rate. 'With measure' 
j scenario 20% increase by 2000 over 1990 levels. Insufficient 
! quantification of measures. 
Italy 436300 12630 2.9 448930 54370 j 'With measure' scenario 1-5% (average 3%) increase by 2000 over 1990 
j levels, as communicated to Commission in Monitoring Mechanism 
| Committee meeting in February 1995. Insufficient quantification of 
I measures. 
Luxembourg 13300 -3200 -24.1 10100 7820 ! 'Without measures' scenario derived based on assumptions of consistent 
j set of fuel prices and GDP growth rate. Insufficient quantification of 
i measures. 
(,) C02 inventory 1990, June 1995. 
(2) Absolute change 1990/2000 based on Member State trajectories. 
(3) 'With measures' scenario, based on C02 inventory for EU-15 1990. These trajectories and projections have been adjusted to be consistent with the same 1990 C02 baseline inventory for 1990. 
<4> Difference between 'with' and 'without' measures scenarios, Member State trajectories. 
tS) Some of the measures are understood in a very broad sense 
The trajectories and projections for 2000 have been adjusted to be consistent with the same 1990 baseline, the Corinair inventory 1990 shown in column (a). For ail but five countries, the Corinair 
inventory figure is higher than the 1990 trajectory baselines used by the Member States. For France, Ireland and Sweden the 1990 trajectory baseline corresponds with the Corinair emission figure for 
1990, while for the Netherlands and the UK the Corinair figure is lower. 
-F Member State 
; Netherlands 
i Portugal 
j Spain 
; Sweden (a) 
C02 Inventory 
1990 (,) 
151800 
42500 
227300 
61300 (b) j (c) 
Change 1990/2000 ! % change 
,a I 199f>/?nnn 
-600 | -0.4 
15300 j 36 
54100 j 23.8 
2 700 j 4.4 (d) 
Trajectory 2000 
AVfth MPiKifrpO (3) 
151200 
57000 
281400 
64000 
j UK j 579800 | -35140 j -6.1 j 544660 
j EU-15 i 3,285,620 j -26430 j -0.8 j 3,260,900 
| '" CO} inventory 1990, June 1995. 
{ (}) Absolute change 1990/2000 based on Member State trajectories. 
! IJ' 'With measures' scenario, based on C02 inventory for EU-15 1990. 
j |4) Difference between 'with' and 'without' measures scenarios, Member State trajectories. 
I 1SI Some of the measures are understood in a very broad sense. 
I The trajectories and projections for 2000 have been adjusted to be consistent with the same 1990 basel 
! inventory figure is higher than the 1990 trajectory baselines used by the Member Slates. For France, Irelan 
; 1990, while for the Netherlands and the UK the Corinair figure is lower. (e) 
Effect of Measures 
10500 
7030 
594 70 
10200 Comments'5* 
'With measures' and 'without measures' scenarios from Energy Policy 
Scenario. Sectoral quantification of measures. 
'Without measures' scenario derived based on assumptions of consistent 
set of fuel prices and GDP growth rate. 'With measures' scenario is 40% 
increase in emissions by 2000 over 1990 levels. No quantified measures. 
'Without measures' scenario is derived based on assumptions of 
consistent set of fuel prices and GDP growth rate. 'With measures' 
scenario is 25% increase by 2000 over 1990 levels. No clear 
quantification of measures. 
'With measure' scenario is 4% increase by 2000 over 1990 levels, not 
temperature corrected, and stabilisation if temperature corrected. All 
measures included in the scenario are quantified. 
71740 j 'With measures'scenario from EP-65, central GDP growth, high fuel j 
'; prices , reduction of 6% by 2000 compared to 1990 levels. All measures ; 
j in scenario quantified. j 
491,290 I ; 
ine, the Corinair inventory 1990 shown in column (a). For all but five countries, the Corinair j 
d and Sweden the 1990 trajectory baseline corresponds with the Corinair emission figure for j 
Table A 2 Alternative Trajectories for the Year 2000 (percentage change 1990/2000) 
Member State (a) 
Member State 
Trajectories/ 
Projections (1) j 00 
Modified Trajectories/ 
Projections m (c) 
Commission 
Projection (J) Notes 
ft Austria 
! Belgium 
! Denmark 
• Finland 
: Fiance 
• Germany 
• Greece 
: Ireland 
j Italy 
j Luxembourg 
! Netneriands 
j Portugal 
j Spain 
j Sweden 
j UK 
I EU-15 1 : 
-1 : 
•12 
30 
-13 j 
14 
20 I 
3 ! 
-24 
0 • 
36 
21 = 
4 j 
-6 j 
-1 ! 3 ! 
33 j 
13 • 
•10 : 
19 : 
25 
6 : 
-20 
10 : 
36 
23 
6 : 
-2 j 
3 j j Growth rates differ marginally but fuel prices assumed in (a) are very high compared to 
I (b) which explains low emission growth in (a). 
I Due to lack of information about GDP growth rate, the assumed growth rate is 0.7% 
j lower than in modified trajectory. 
GDP growth assumptions differ marginally between the (a) and (b) but fuel prices are 
very high in (a) and price elasticity is very high, leading to fall in emissions in (a). 
j Lower GDP growth rate and higher fuel prices in (a) than in (b) but the income effect 
j is higher leading to higher emissions in (b). 
! GDP growth rate lower and fuel prices higher in (a) than in (b), leading to lower 
j emissions in (b)(a) 
j Due to lack of information about growth rate, it is assumed to be 0.7% lower than in 
j modified trajectory. 
{ Due to lack of information about growth rate, it is assumed to be 0.7% lower than in 
j modified trajectory. 
j Due to lack of information about growth rate, it is assumed to be 0.7% lower than in 
j modified trajectory. 
| Much higher GDP growth rate in (b) than in (a) and higher fuel price increase. Income 
I effect outweighs price effect leading to higher emissions in (b). 
! Growth rate in (a) lower than in (b). Fuel prices are the same. Emission reduction 
j greater in (a). 
j Higher GDP growth rate in (b) than (a) and high income elasticity explains higher 
j growth in emissions. Fuel prices higher in (a) than in (b). 
Due to lack of information about growth rate, it is assumed to be 0.7% lower than in 
modified trajectory. 
i Lower growth rate and higher fuel prices in (a) than in (b), explains higher emissions 
! in(b). 
j Lower growth rate and higher fuel prices in (a) than in (b). Price effect dominates 
| leading to lower rise in emissions in (a). 
j Higher GDP growth rate in (b) leading to higher emissions than in (a). 
5.4 I Aggregate figure for EU-total. 
j (1) Trajectory 
j (2> Trajectory 
: (3) Trajectory 
tammmsmam 1990/2000, based on Corinair COz inventory (column (c) in Table Al). 
1990/2000, based on modified common assumptions for GDP and fuel prices. 
1990/2000 from Commission Services (DGXVII), Conventional Wisdom scenario 2020. 
HHSHHBHHH^MHHaMHBBnBnBHnBHiHBBKEHHKHHHaaHaHMH 
Annex B 
Country Summaries 
x> 
AUSTRIA 
j 1990 Emissions (GgC02) ! Trajectory 1990/2000 on C02 j Effect of Measures (GgC02) 
j j inventory baseline (%) I 
Member State Trajectory (1) | 59200 \ 0.6 j 5520 
Modified Trajectory j I 8 I 
Target/Objective and Comments: - Stabilization scenario (by 2000) 
- Reduction target committed to : 20% by 2005 based on 
emission in 1988 (Toronto target) 
Summary of measures: Most measures focus on reducing end use energy consumption rather than on fuel 
switching. The quantified measures are geared towards the promotion of renewables for heating purposes, 
through subsidies and tariff restructuring. The same instruments are used to promote district heating. 
Attention is also given to reducing energy consumption in the transport sector, for example a vehicle tax 
which reflects fuel consumption. Measures geared towards industry are largely voluntary. Measures to 
enhance sinks include afforestation, forest management, increase in long-lived wood products. 
Quantified measures 
j Use energy of surplus straw (agricultural, district heating and j 0.60 MtC02 
j building subsidies; regulations on supply of electricity to public ; 
! grid j 
Use of biogas as fuel and raw material (district heating and j 2.90 MtC02 
building subsidies; regulation on supply of electricity to public j 
grid j 
! Use of solar energy especially for water heating; use of solar ! 0.60-1.30 MtC02 
j collectors; passive solar energy use (subsidies, building j 
j regulations) j 
TOTAL 4.10-4.80 MtCO, 
Categorisation of measures: The measures are divided into measures under implementation, measures which 
are planned to be undertaken under the next legislative period (1994-1998) and measures at the conceptual 
stage. The quantified measures are all under implementation. 
Projected C02 emissions in 2000 relative to target(2): In the with measure scenario (3), Austria expects to 
stabilise C02 emissions by 2000. It is not clear which measures are included in the projection. The 
assumption made is that energy savings and structural changes will reduce emissions, but only a third of the 
potential is realised. Energy and carbon intensity are assumed to fall by 2.1% and 0.5% respectively per 
year to 2005. If the measures which are planned for the legislative period 1994-1998 are required for 
stabilisation, the outcome will only be secured if implementation is begun immediately. Measures in the 
conceptual phase are not likely to have an impact before the year 2000. This projection can also be put in 
question by the fact that very high fuel prices have been assumed for 2000. 
The new government has expressed a political will to introduce a C02 tax by 1996. Depending on the 
timing and the rate at which the tax is introduced, it could make a substantial contribution to meeting the 
stabilisation target. 
(1> Adjusted to be consistent with the same 1990 baseline, the C02 inventory for the EU-15. 
<2) The discussion is based on Member State trajectories, not applied to the inventory for the EU-15. Therefore there may be small discrepancies between the figures 
mentioned in the text and the figures provided in the box under Member State Trajectory above 
(3) Stabilisation scenario (STAB). 
2} 
BELGIUM 
1990 Emissions (GgC02) j Trajectory 1990/2000 on C02 j Effect of Measures (GgC02) 
j inventory baseline (%) I 
Member State Trajectory (1) j 114500 I -1.1 j 13630 
Modified Trajectory j | 3 j 
Target/Objective and Comments: 5% reduction by 2000 compared to 1990 level. Temperature corrected 
target. 
Summary of measures: Greatest impact expected from increased efficiency in electricity generation and shift 
to electric steel industry. Substantial impact also expected in the residential sector through a broad range of 
measures of different types and effects including: promotion of cogeneration (combined heat & power); 
promotion of energy efficiency household appliances and discouragement of electric heating; fiscal 
instruments include changes to tax benefits and parking fees in the transport sector, and grants to encourage 
energy conservation in public buildings. No measures to enhance sinks. 
Quantified measures 
11. j Improvement of insulation in new buildings in the residential j 0.40 MtC02 j 
! j and commercial sectors j j 
! 2. j Increased use of natural gas, improved performance of heating j 1.90 MtC02 
j | installations and hot water boilers j j 
j 3. I Promotion of energy efficiency household appliances and j 0.75 MtC02 j 
; I lighting j j 
; 4. j Discouraging of use of electric heating j 0.10 MtC02 j 
j Subtotal for residential/commercial sector j 3.15 MtC02 
j 5. ; Transport plans for company employees j 0.125 MtC02 j 
! 6. j Reduced access by passenger and transport vehicles to city j 0.12 MtC02 ! 
j j centres I : 
! 7. I Other measures for the promotion of public transport in urban j 0.10 MtC02 j 
• : areas j ! 
8. ! Reduced road transport j 0.05 MtC02 
9. ; Fiscal policy in transport j 0.75 MtC02 
10. ; Increased enforcement of speed limits j 0.60 MtC02 
j Subtotal for transport j 1.75 MfC02 
11. ! Measures in the industrial sector: energy audits for suppliers j 0.64 MtC02 
12. j Promotion of renewable energy j 0.20 MtC02 
13. j Promotion of cogeneration j 2.00 MtC02 
: Subtotal of all additional measures j 7.74 MtC02 
14. j Shift towards electric steel production (implemented) : 2.00 MtC02 
15. ! Increased efficiency in electricity production ; 4.00 MtC02 
TOTAL 13.74 MtCO, 
Adjusted to be consistent with the same 1990 baseline, the C02 inventory for the EU-15. 
Categorisation of measures: The measures have been divided into those which are currently being 
implemented (adopted before 1994), complementary measures which are the focus of the plan (to be 
implemented after 1994), and other associated measures which are for the longer term. The two most 
important measures under implementation are the technical improvements to the nuclear plants and the 
installation of electric steel works. The quantified measures fall into the complementary measures category. 
They have, however, been subject to a ministerial decision. 
Projected C02 emissions in 2000 relative to target(1): Belgium has clearly stated that in the absence of a 
C02 tax, the target will not be reached, it will just do a little better than stabilisation (2). With a C02 tax, 
however, the 5% reduction target for 2000 could be reached. The tax is expected to reduce emissions by 
7%-10%. Belgium is considering implementing a C02 tax in 1995. 
implementation of some of the quantified measures is uncertain and sometimes for the longer term, e.g. 
voluntary measures in industry and measures in the transport sector which are dependent on the development 
of public transport. If the measures are to have an impact before 2000, implementation must be initiated 
immediately. 
(,) The discussion is based on Member State trajectories, not applied to the inventory for the EU-15. Therefore there may be small discrepancies between the figures 
mentioned in the text and the figures provided in the box under Member State Trajectory above. 
(2) Two projections presented. Bureau de Plan and Centre d'étude économiques de la KUL, and although they provide a range, they show largely the same result 
DENMARK 
1990 Emissions (GgC02) j Trajectory 1990/2000 on C02 j Effect of Measures (GgC02) 
! inventory baseline (%) j 
Member State Trajectory (1) j 52100 j -11.9 ! 13500 
Modified Trajectory j j 7 j 
Target/Objective and Comments: Target for C02 emissions adjusted for imports of electricity in base year, 
i.e. C02 emissions are calculated on the assumption that all electricity was generated in Denmark in base 
year. Using unmodified data, the target is equivalent to a rise of 6.4% over 1990 levels. 
Denmark imports electricity from Norway and Sweden but the quantity varies over time depending on water 
availability and therefore the level of production from hydro sources in the two exporting countries. 
Denmark has a largely fossil fuel based energy supply system whereas Norway and Sweden have high 
contributions from hydro and nuclear (Sweden only). In 1990 Denmark imported significant quantities of 
electricity. Therefore its C02 emission levels were lower than might be expected in a typical year, and 
10.7% lower than if all electricity had been generated in Denmark. 
Summary of measures: Efficiency improvements in end use through the implementation of efficiency 
standards for electrical appliances and other equipment are expected to make a large contribution to C02 
reductions. Also important is promotion of CHP through subsidies. New generating capacity will come 
from construction of gas-fired plants after 2000. Denmark has a C02 tax in place and it was recently 
increased. Then intention is to introduce more green taxes in all the sectors of the economy. In the 
transport sector emphasis is on promoting public transport, e.g. investment support for purchase of clean 
vehicles. Other measures include promotion of energy efficient driving through information and training and 
promotion of rail transport. No measures to enhance sinks. 
Quantified measures: (a more detailed breakdown is only available for the year 2005) 
: 1. ! Oil & gas (refineries, North Sea) ; 0 j 
: 2. j Transport j 0 j 
i 3. | Energy Sector \.J}.:?}$£2l\ 
j TOTAL 13.5MtC02 j 
Categorisation of measures: The measures are included in a set of plans which have been adopted by 
government: the 1990 action plans for energy and transport respectively, the 1992 action plan on waste and 
recycling, the 1993 follow up on the 1990 energy action plan, and the 1993 white paper on transport. The 
quantified energy measures are all included in the 1993 follow up energy plan. No measures for the 
transport sector have been quantified. In a separate communication to the Commission it has been 
announced that a set of green taxes will be introduced. 
Projected C02 emissions in 2000 relative to target(2): Based on the 'with measures scenario' (3), Denmark 
will reach the* 5% reduction target (corrected for electricity imports) if all the measures included in the 1993 
follow up action plan are implemented. The reduction will come from the energy sector. The effect of 
measures in the transport sector is assumed to be nil and emissions are expected to increase in this sector 
between 1990 and 2000. 
In an official note to the Commission, Denmark announces that it has problems implementing two important 
measures: the introduction of efficiency standards and appliances due to delays relating to the EU directive 
on efficiency standards; and the conversion of electrically heated buildings to central heating by gas or 
district heating since a voluntary agreement with the power industry has not yet been reached. 
(" Adjusted to be consistent with the same 1990 baseline, the C02 inventory for the 1£U-I 5. 
(2) The discussion is based on Member State trajectories, not applied to the. inventory for the EU-15. Therefore there may be small discrepancies between the figi 
mentioned in the text and the figures provided in the box under Member State Trajectory above 
0) Revised estimate, June 1995, showing total domestic energy emissions 1990-2000, including flaring. 
S* 
Regarding standards for household appliances, the proposed EU Directive on refrigerators is less ambitious 
than foreseen Danish standards, both as regards the stringency of the standards and the timing (it would 
enter into force after 2000). This measure may therefore be lost to the Danish national plan. The two 
measures were together expected to contribute 3% of the C02 reduction planned for 2005. 
In the note to the Commission, Denmark also presented a set of new green taxes which have been adopted 
by Parliament and will enter into force in 1996: an S02 tax (1.5 ECU/kg S02); a C02 tax on natural gas; 
an increased C02 tax on energy for industrial processes and commercial energy use (including electricity), 
with one rate for light processes (13ECU/t C02) and a virtually vanishing rate (0.5ECU/t) for energy 
intensive processes. The low rate will be conditioned on the implementation of an energy audit and 
voluntary agreements on energy savings. Without such an agreement, the default tax is 3.5 ECU/t C02. 
The rather elaborate system of exemptions and recycling is necessary to avoid losing competitiveness vis a 
vis other European countries that have not introduced a similar tax. Until this problem is overcome, 
Denmark cannot exploit the full potential of the C02 tax instrument. 
The trajectory can be questioned by the fact that the assumed fuel prices and price elasticity very high, both 
factors contributing to a large estimated C02 emission reduction. 
^\ 
FINLAND 
1990 Emissions (GgC02) j Trajectory 1990/2000 on C02 j Effect of Measures (GgC02) 
| inventory baseline (%) j 
Member State Trajectory (1) j 53900 \ 29.7 j 9000 
Modified Trajectory ! I 33 ! 
Target/Objective and Comments: The Finnish target is to 'stop growth in energy related C02 emissions by 
the end of the century'. Finland has no base year for its target which makes it unclear in numerical terms. 
Summary of measures: The national communication is based on Government programmes approved in the 
1990s that relate to climate change policy. Some programmes were approved specifically to implement 
climate change policies but some were adopted for other reasons. A main focus of the C02 strategy is 
energy conservation in end-use, to be achieved to a large extent through economic instruments. Finland has 
C02 tax (since 1990) and energy taxes in place, encouraging fuel switching, energy conservation, use of 
renewables, and changes in production and consumption patterns. Other measures to encourage energy 
conservation include voluntary agreements with industry and information and education. Promotion of 
biofuels is important (aim to increase consumption by 25% by 2005 over 1994 levels). Measures used in 
the transport sector have mostly been fiscal and economic instruments aimed at reducing fuel consumption 
and encouraging modal shift. A new action programme for transport has been adopted aiming at restraining 
growth in traffic; a mam tool is economic instruments. Measures to enhance sinks are important and focus 
on forest management and commercialisation of wood products. 
Quantified measures 
I Increased C02/energy tax (to FIM 38.30/tonne C02 and FIM j 2000 Gg C02 
j 3.50/MWh. j 
| Energy conservation programme, including a gradually [ 6000-8000 Gg C02 
; increasing energy tax. j 
| Promotion of biofuels (25% increased consumption by 2005 j 3000 Gg C02 
j over 1994 levels). j 
I Energy technology development programmes (1993-1998) to j 1000-5000 Gg C02 
j develop technology for renewable energy sources through j 
; financing of demonstration projects and R&D. j 
TOTAL 12000-18000 Gg C02 
Categorisation of measures: The majority of the Finnish measures in the national communication have been 
approved by Parliament and are under implementation (e.g. efficiency improvements in energy production 
and end-use and energy and carbon taxes). All of the quantified measures are under implementation. A 
second category of measures, mainly aimed at the transport sector, have also been adopted by Parliament, 
but the stage of implementation is unclear. 
Projected C02 emissions in 2000 relative to target<2): Based on the 'with measure scenario' (3), Finland will 
increase emissions by 16% in 2000 over 1990 levels. This takes account of effects of energy taxation, 
energy conservation (some overlap in the figures noted above), increased use of bio-energy and the adoption 
of new technologies (some overlap in the figures noted above). 
' Adjusted to be consistent with the same 1990 baseline, the C02 inventory for the EU-15. 
1 The discussion is based on Member State trajectories, not applied to the inventory for the EU-15. Therefore there may be small discrepancies between the figures 
lentioned in the text and the figures provided in the box under Member State Trajectory above. 
' 16% is the median of a range given as the 'with measures scenario' (10-22% increase). 
32-
The electricity import situation and the structure of the electricity production capacity is currently being 
reviewed. Finland has consistently imported a large share of its electricity from neighbouring countries but 
there are major uncertainties and conditions attached to continuing doing so. In the next few years Finland 
will have to decide how it is going to produce the base load capacity needed. The expected increase in 
emissions in Finland is largely due to the assumption that electricity imports are replaced with domestic 
production capacity. Depending on the choices that are made regarding domestic base load capacity, the 
increase in emissions could range from 10-22% (16% mentioned above is the median). Recent estimations 
show, however, that the total increase in domestic electricity production capacity in 2000 would not likely 
be met by coal fired power plants. The additional reduction would largely come from restructuring the 
electricity market. The effect of measures are also influenced by the fact that Parliament has decided against 
the construction of a fifth nuclear power plant. No additional nuclear power plants are likely to be 
constructed in Finland in the near future. 
The impact of the C02 tax is reduced by the lack of action at the international level; for reasons of 
competitiveness the tax remains too low to fully exploit the potential of the measure. The effect of energy 
taxation is also hampered by the lack of international coordination. 
The trajectory assumes rather low GDP growth and high fuel prices, but the assumed income elasticity is on 
the high side. The effect on estimated emissions might cancel out. 
A3> 
FRANCE 
1990 Emissions (GgC02) ! Trajectory 1990/2000 on C02 j Effect of Measures (GgCOj) 
I inventory baseline (%) ! 
Member State Trajectory (I) j 366500 8.5 I 73200 
Modified Trajectory | j 13 | 
EU target and comments: The initial target was stabilisation at less than 2 tC (7.3 tC02) per capita per year 
by 2000. This is equivalent to a 13% increase relative to 1990 levels, i.e. projected 59.29 million population 
in 20Ô0. Although this general commitment is still valid, the French have declared that it should no longer 
be considered as a specific target for the year 2000. Instead there is a commitment to the introduction of 
measures which should be coordinated and designed relative to a common reference of marginal cost of 
emission abatement. France suggests that this approach should be taken within the EU as a whole in order to 
"share" the current stabilisation target, and at the international level in the context of the Berlin Mandate. 
This target is difficult to express in numerical terms. 
Summary of measures: The French Communication recalls that energy policy in France since the first oil 
shock has already made it possible to significantly reduce C02 emissions (more on a per capita basis 
between 1980-1990 than most other EU countries). Bearing this in mind, the French communication 
underlines the importance of achieving comparable cost of measures (per tonne of carbon emissions avoided) 
across the Member States. 
Emphasis on energy conservation and fuel switching. Measures include: demand-side management to 
reduce peak demand generally met by fossil-fuel generation; tax benefits for industry energy efficiency 
improvements; road tariff increases; subsidies for rail transport. Measures to enhance sinks include 
afforestation, land-use change (CAP reform) and promotion of wood in construction. 
Quantified measures: No link between quantification of measures and projection. The information given in 
the National Communication is not sufficient to derive a quantitative estimation of the global effect of the 
set of measures. 
Categorisation of measures: The state of implementation of measures remains an uncertainty as the effort 
made by France is linked to the marginal effort (expressed in ECU/t of equivalent carbon) accepted by other 
Member States. It would seem that the expected impact is largely expected after 2000. 
Projected C02 emissions in 2000 relative to target<2): According to the 'with measures scenario', emissions 
are expected to increase by 7% in 2000 over 1990 levels. It is very hard to assess the uncertainty pertaining 
to this projection since it is not clear which measures should contribute to the expected emission reductions. 
The assumption made is that voluntary energy saving measures such as those described in the 
communication, are undertaken. The uncertainty is increased by the fact that the assumptions made in the 
trajectory about GDP growth rates seem low while the assumptions about fuel prices seem high, thus 
yielding lower emission projections for 2000 (see comparison with modified trajectory in Table A2 or the 
box above). 
"' Adjusted to be consistent with the same 1990 baseline, the C02 inventory for the EU-15. 
(2) The discussion is based on Member State trajectories, not applied to the inventory for the EU-15. Therefore there may be small discrepancies between the figures 
mentioned in the text and the figures provided in the box under Member State Trajectory above. 
3>T 
GERMANY 
1990 Emissions j Trajectory 1990/2000 on j Effect of Measures 
(6gC02) I C02 inventory baseline (%) j (GgC02) 
Member State 1013000 -13 144330 
Trajectory(1) \ 
Modified Trajectory -10 
Target/Objective and Comments: 25% reduction compared to 1990 levels by 2005. Germany has yet to set 
a target for the year 2000. The measures described in the German Communication are intended to have an 
impact by 2005. However, they can be expected to have an effect on emissions already by the year 2000 
(possibly contributing to a C02 emission reduction in order of magnitude of 13-15% as was mentioned by 
the German delegate at the fifth Monitoring Committee meeting on 18 May, 1995 and reported in the August 
1995 update report to the Commission), although the full effect of measures tend to be achieved in the final 
implementation stages rather than pro rata throughout the implementation period. 
Summary of Measures: A very broad range of measures targeting all sectors. Some of the main measures 
implemented now are : 
- Federal government / lander district heating modernisation programme for the new Bundeslânder 
- Act on the sale of electricity to the GRID 
- Support for local and regional climate protection concepts 
- Funding for the use of renewable energies 
- Tax breaks for cogeneration under the mineral-oil tax act 
- Increase of the mineral-oil tax 
- Emissions-oriented motor-vehicle : tax 
- Federal traffic infrastructure plan 
- Railway structural reform 
Measures to enhance sinks include afforestation and forest conservation. 
Quantified measures: No measures have been quantified. 
Categorisation of Measures: 115 measures listed, 92 of which have been or are under implementation. 21 
measures are planned and await adoption. 
Projected C02 emissions in 2000 relative to target(2): Given that Germany has not provided a trajectory or a 
quantification of measures, it is difficult to assess where emissions could be in 2000. In the Monitoring 
Mechanism Committee Germany announced it expected to reduce emissions by 13-15% by 2000 compared 
to 1990 levels (3). It is not clear which measures need to be implemented to achieve this emission reduction 
or what the current level and effort of implementation is. Given that Germany is a key contributor to C02 
emissions in the Community, this uncertainty regarding the effect of measures and the level of emissions in 
2000, has a significant influence on the level of uncertainty of the assessment of progress towards the 
Community C02 target. 
Germany has stated that it will have difficulties reaching the national target (-25% by 2005 compared to 
1990 levels) unless a C02/energy tax is introduced at the Community level. In this report the assumption 
has been made that the 13% reduction does not take account of a C02/energy tax.. 
m Adjusted to be consistent with the same 1990 basel i ne, the C02 inventory for the EU-15. 
<2) The discussion is based on Member State trajectories, not appl ied to the inventory for the EU-15. Therefore there may be 
small discrepancies between the figures mentioned in the text and the figures provided in the box under Member State 
Trajectory above. 
(3> Monitoring Mechanism Committee meeting, May 1995. 
GREECE 
1990 Emissions (GgC02) j Trajectory 1990/2000 on C02 I Effect of Measures (GgC02) ! 
j inventory baseline (%) j j 
Member State Trajectory (I) j 86100 j 14.3 ! 9590 
Modified Trajectory j j 19 I 
Target/Objective and Comments: Greece has no official target. In the national communication it has set the 
'realistic objective' to restrict the total increase in C02 emissions between 1990 and 2000 to 15% (with a 
margin of error of +/-3%). 
Summary of measures: The C02 strategy is mainly composed of an energy conservation policy covering all 
sectors and promotion of natural gas and renewable energy sources. In the domestic sector energy 
conservation measures include energy efficient building/equipment design, new lighting technologies and 
boiler maintenance. In industry the conservation measures include improvement in auxiliary operations and 
production modernisation. Measures in the transport sector include promotion of alternative fuels, improved 
vehicle maintenance, traffic management and development of public transport. No measures regarding the 
enhancement of sinks (only in conceptual phase). 
Quantified Measures: 
ll. ! Introduction of natural gas in electricity generation. [ 4.2 Mt COz 
j 2. j Introduction of natural gas in industry. j 0.7 Mt C02 j 
j 3. j Introduction of natural gas in residential-commercial-service j l.lMtC02 ; 
j j sector. I I 
! 4. j Promotion of CHP. j 0.2 Mt CO, j 
j 5. ; Improvement in lignite-fired power stations. j 0.3 Mt C02 j 
j 6. ! Promotion of wind farms. j 1.0MtCO2 j 
! 7. I Promotion of solar energy applications. j 1.0 Mt C02 j 
j 8. j Promotion of biomass utilisation. j 0.9 Mt C02 
j 9. ; Promotion of small hydroelectric works. j 0.2 Mt C02 j 
j 10. j Promotion of geothermal energy utilisation. j 0.06 Mt C02 j 
! 11. ! Renewable energy pilot projects. j 0.1MtCO2 j 
j 12. j Energy efficient building/equipment design for household and j 0.0 Mt C02 j 
j j tertiary sector. I ! 
! 13. I New lighting technologies for household and tertiary sector. j 0.7 Mt C02 j 
! 14. | Boiler maintenance in household and tertiary sector. \ 0.4 Mt C02 j 
! 15. I Improvement in auxiliary operations in industry. ; 0.5 Mt C02 j 
j 16. I Production modernisation in industry. j 0.8 Mt C02 j 
i 17. I Promotion of alternative fuels in transport. j 0.05 Mt C02 j 
j 18. j Improved maintenance of vehicles and use of more energy j 0.3 Mt COz j 
| ! efficient vehicles. ! j 
! 19. | Rational management of transport system. j 0.45 Mt C02 j 
| 20. j Up-grading and modernisation of public transport. j 0.4 Mt C02 J 
| TOTAL 13.4 Mt COz j 
(,) Adjusted to be consistent with the same 1990 baseline, the C02 inventory for the EU-15. 
Categorisation of Measures: The plan focuses on measures which have already been adopted 
by the Government. 
Projected C02 Emissions in 2000 Relative to Target/Objective1: In the most realistic scenario, 
Greece estimates that it will increase its emissions by 15 % ,+/- 3% by the year 2000 
compared to 1990 levels if the measures quantified above are introduced. The underlying 
assumption is that the measures in the power generation sector has a 100% impact but that 
the penetration of natural gas and other measures only have a 75% and 67% impact 
respectively. 
In a worst case scenario, emissions could increase by 18% in 2000 compared to 1990 levels. 
This could happen if there is a major failure on the part of administration particularly 
regarding the funding of the implementation of measures, if the funds have not been 
distributed as they should or if they have been misused. Other problems that could arise are 
delays in the construction of natural gas power plants or drastic changes in the demand for 
energy e.g. through the spreading of air-conditioning to the whole domestic sector. 
In a best case scenario, the increase in emissions could be limited to 12%. This could happen 
if the power generation sector accelerates the introduction of new technologies in the lignite-
fuelled stations, if the penetration of natural gas was 100% successful by 2000, if gas-fired 
stations are used to meet base load, if a target is set to achieve maximum possible substitution 
to natural gas in the household and tertiary sector, if availability of private funding for the 
promotion of renewables is larger than expected, if the energy efficient technology available 
on the market penetrated the household and tertiary sector, if energy efficiency standards and 
labelling are introduced, and if public funding is made available for investment in core 
infrastructure. 
While models show that the effect of a C02 tax of between $3-$10/bbl, would have a limited effect 
on the level of C02 emissions, such a tax could increase the availability of public funding for the 
financing of technological interventions. That would secure the outcome of the most likely scenario, 
namely a 15% emission increase, and improve the chances of achieving the best case scenario, an 
increase of only 12%. 
1 The discussion is based on Member State trajectories, not 
applied to the inventory for the EU-15. Therefore there may be 
small discrepancies between the figures mentioned in the text and 
the figures provided in the box under Member State Trajectory 
above. 
i~\ 
IRELAND 
1990 Emissions (GgC02) j Trajectory 1990/2000 on C02 ! Effect of Measures (GgC02) 
j inventory baseline (%) j 
Member State Trajectory (1) | 30720 j 20.5 j 1390 
Modified Trajectory j I 25 j 
Target/Objective and Comments: Ireland has no official target but an objective of limiting the increase in 
emissions to 20% above 1990 levels by 2000. 
Summary of measures: Emphasis on energy conservation plus government action on fuel switching. 
Measures include combined heat and power projects, promotion of alternative energy sources, construction 
of efficient peat-fired power plant, establishment of an energy centre to coordinate the energy conservation 
programme, information campaigns for energy conservation, improved insulation in buildings, development 
of public transport in urban centres. Industry will contribute to reducing C02 emissions through voluntary 
agreements. Measures aimed at enhancing sinks include afforestation and reafforestation. 
Quantified Measures: 
\ Demand-side management in domestic, tertiary and industrial j 0.27 Mt C02 
I sector. j 
! TOTAL 0.27 Mt CO, 
Categorisation of Measures: Most measures described in the plan are under implementation, including those 
aimed at enhancing sinks. 
Projected C02 Emissions in 2000 Relative to Target/Objective (2>: Ireland estimates that by implementing 
the measures described in the plan, it can limit the increase in C02 emissions to 20% over 1990 levels. This 
assessment does not take account of the potential introduction of a combined C02/energy tax. 
Ireland was the fastest growing economy in the OECD area in 1994 (3) and the ability to meet the 20% 
objective and maintain emissions at that level is more linked to the future level of economic growth than to 
the implementation of the measures in the C02 strategy. 
(,) Adjusted to be consistent with the same 1990 baseline, the C02 inventory for the EU-15. 
<2) The discussion is based on Member State trajectories, not applied to the inventory for the EU-15. Therefore there may be small discrepancies between the figures 
mentioned in the text and the figures provided in the box under Member State Trajectory above. 
m OECD Economic Outlook (57), June 1995. 
ITALY 
; ! 1990 Emissions (GgC02) j Trajectory 1990/2000 on C02 j Effect of Measures (GgCOj) j 
j j } inventory baseline (%) j ! 
| Member State Trajectory (1) j 436300 I 2.9 ] 54370 j 
I Modified Trajectory j j 6 j ! 
Target/Objective and Comments: Stabilisation at 1990 levels by 2000. 
Summary of measures: Broad range of measures including decommissioning of oil-fired electricity plant 
and establishment of gas-fired generation; new investment in renewables; traffic limitation measures; 
encouragement of public transport; new energy efficiency standards for the household sector; voluntary 
agreements with industry for environmental quality improvements. The measures aimed at enhancing sinks 
focus on reforestation, forest management and promotion of forest and brushwood products. 
Quantified measures: No quantified measures. 
Categorisation of measures: Measures divided into those which are already adopted and additional 
initiatives to limit C02 emissions. The former category includes measures for the power generation sector 
(NEP 1988) and measures for co-generation and auto-production, which were adopted independently of the 
C02 limitation strategy. The latter category includes measures for the residential/commercial and transport 
sector and for industry. 
Projected C02 emissions in 2000 relative to target(2>: Italy does not expect to stabilise emissions in 2000 
(overshoot of 1-5%). It is not clear which measures are in included in this trajectory or what the stage of 
implementation is of the measures described in the C02 strategy. In spite of this uncertainty, the calculated 
effect of measures is very high. Based on the imprecise information in the national communication, it is 
difficult to understand how Italy plans to achieve even its projected emission level. Italy has stated that 
stabilisation can only be achieved if a C02/energy tax is introduced at Community level. 
Considering that Italy is one of the main contributors to Community C02 emissions, this uncertainty 
regarding its emissions in 2000 has an important influence on the assessment of progress towards the 
Community target. 
' Adjusted to be consistent with the same 1990 baseline, the C02 inventory for the EU-15. 
» The discussion is based on Member State trajectories, not applied to the inventory for the EU-15. Therefore there may be small discrepancies between the figures 
lentioned in the text and the figures provided in the box under Member State Trajectory above. 
2°l 
LUXEMBOURG 
Member State Trajectory (1) 
Modified Trajectory 1990 Emissions (GgC02) 
13300 Trajectory 1990/2000 on C02 
inventory baseline (%) 
-24.1 
-20 Effect of Measures (GgC02) I 
7820 
Target/Objective and Comments: Stabilisation by the year 2000 at 1990 levels. 
Summary of measures: The plan focuses on the power generation sector and the transport sector. Some 
measures include feasibility studies on the use of gas vapour turbines, pilot project with gas turbine and 
hydro power, introduction of cogeneration in buildings and investigation of other uses of cogeneration, 
investigation of potential for renewable energy sources, promotion of public transport, development of 
intermodal freight transport, promotion of rail transport and internal waterways, investigation of vehicle tax 
based on energy consumption. Luxembourg is also considering to introduce a C02 tax. No measures to 
enhance sinks. 
Quantified Measures: None. 
Categorisation of Measures: Measures which fall in the category under implementation include for the most 
part the legislative framework for environmental policy and certain subsidies for energy efficiency measures 
in the domestic sector. The majority of the measures are planned, including measures for the power 
generation sector and the transport sector. Some are even on a conceptual stage. The most important 
'measure' is the restructuring of the steel industry which will make the principal contribution to reducing C02 
emissions but which is being undertaken for other policy reasons than climate change. 
Projected C02 Emissions in 2000 Relative to Target/Objective <2): Luxembourg expects C02 emissions to 
fall by 33% by 2000 compared to 1990 levels. The bulk of the reduction comes from the restructuring of 
the steel industry, where electric steel works will replace old steel works. This restructuring has already 
been initiated and is well under way. The construction of a gas-vapour turbine for residential heating is 
planned. There is no reason to believe that the 33% reduction will not be achieved in 2000. 
(1) Adjusted to be consistent with the same 1990 baseline, the C02 inventory for the EU-15. 
(2) The discussion is based on Member State trajectories, not applied to the inventory for the EU-15. Therefore there may be small discrepancies between the figures 
mentioned in the text and the figures provided in the box under Member State Trajectory above. 
NETHERLANDS 
1990 Emissions (GgC02) j Trajectory 1990/2000 on C02 j Effect of Measures (GgC02) 
! inventory baseline (%) j 
Member State Trajectory (1) ] 151800 j -0.4 j 9900 
Modified Trajectory J j 10 j 
Target/Objective and Comments: Temperature corrected target is reduction of 3% . 
1990 was an unusually warm year so emissions from space heating were lower than in a normal year. The 
Dutch inventory for 1990 on which the target is based has been adjusted using degree-day statistics to 
produce a 1990 total which is 3.8%' higher than actual emissions. This means that the Dutch target, a 3% 
reduction from 1990 temperature corrected levels, is equivalent to a 0.7% increase over unadjusted 
emissions. Since the Community inventory for 1990 is not temperature corrected, it is more appropriate to 
refer to the non-temperature corrected target which is generally accepted to be a "return to target". 
Summary of measures: Focus on energy conservation and energy efficiency improvements using voluntary 
agreements in the industrial, agricultural and public sectors. The plan includes the following measures: 
investment in cogeneration and subsidies for renewable energy; voluntary agreements for energy 
conservation in industry, public and agricultural sectors; energy conservation programme for SMEs; energy 
efficiency standards and regulations for households and buildings; demand-side management based on 
subsidies and information. Fuel taxes have been introduced and the rate is determined on the basis for 
energy and carbon content. A legislative proposal is being considered to increase the C02 rate for small 
consumers, but it is considered that unless there is progress on an EU tax, the rate for large consumers must 
remain unchanged. Measures in transport sector taken for other reasons than climate change but include 
vehicle related measures to improve energy efficiency, limiting growth of mobility by using economic 
instruments, encouraging modal shift through a comprehensive investment programme in infrastructure, 
promotion of intermodal freight transport. Measures to enhance sinks include afforestation and land-use 
change under CAP. 
Quantified Measures: 
! TOTAL 9900 Gg j 
Categorisation of Measures: The measures described above have been approved by Parliament and 
necessary funds for the implementation of the measures have been set aside in the annual budget. Some 
important measures are already under implementation, primarily the voluntary agreements for industry and 
agriculture. In industry 20 agreements and 9 declarations of intent are in place, covering 75% of industrial 
energy use. In agriculture, the agreement with glasshouse horticulture covers 85% of agricultural energy 
use. 
However, the measures in the transport sector have been implemented for other reasons than climate change. 
Although there is a commitment to implement the transport measures before 2000, there is no defined time 
frame for the implementation. 
Measures under consideration include the introduction of a regulatory tax on energy. Other measures under 
consideration include efficiency requirements for electric appliances and efficiency requirements for 
passenger cars, both at Community level. 
Projected C02 Emissions in 2000 Relative to Target/Objective (2): If the above mentioned measures are 
implemented, then the Netherlands could stabilise emissions at 1990 levels by 2000, based on unadjusted 
figures which is the equivalent of just over a 3% reduction in emissions using temperature adjusted figures. 
The contribution of the transport sector to this reduction is assumed to be zero, so the uncertainty related to 
the implementation of the measures in that sector does not influence projected emission levels in 2000. 
(1) Adjusted to be consistent with the same 1990 baseline, the C02 inventory for the EU-15. 
m The discussion is based on Member State trajectories, not applied to the inventory for the EU-15. Therefore there may be small discrepancies between the figures 
mentioned in the text and the figures provided in the box under Member State Trajectory above. 
PORTUGAL 
1990 Emissions (GgC02) j Trajectory 1990/2000 on C02 j Effect of Measures (GgC02) 
! inventory baseline (%) ! 
Member State Trajectory (l) j 42500 j 36 | 7030 
Modified Trajectory j j 36 [ 
Target/Objective and Comments: Portugal has no official target but an 'objective' to limit the increase in 
C02 emissions to 40% over 1990 levels. 
Summary of measures: The plan presents a broad range of measures, for all sectors. The measures include 
the introduction of natural gas, CHP, improved efficiency in power generation, energy conservation in end-
use, subsidies and information campaigns for energy efficiency improvements in industry, promotion of rail 
transport, modernisation of road infrastructure, traffic management. Measures to enhance sinks include 
forest maintenance, afforestation, forest protection. 
Quantified Measures: None. 
Categorisation of Measures: Measures under implementation include those for the energy, industrial and 
residential sectors which are linked to programmes (often EU programmes) that have been in place for some 
time. The stage of implementation of the measures in the transport sector is unclear, but it would seem that 
they are only in the conceptual or at best in the planned phase. 
Projected C02 Emissions in 2000 Relative to Target/Objective (2}: Assuming that all of the measures 
included in the plan are implemented, Portuguese C02 emissions are expected to increase by 40%. 
However, it would seem that the implementation of the measures in the transport sector is uncertain. Since 
it is not clear to what extent the transport sector is expected to contribute to limiting the increase in C02, it 
is difficult to assess the impact of this uncertainty on the expected emission level in 2000. However, as in 
the other cohesion countries, emission levels are more linked to economic growth than to the implementation 
of the measures included in the C02 strategy. The actual increase in emissions between 1990 and 1993, 
years of low economic growth, indicates that a lower increase than 40% could be achieved in 2000. 
> Adjusted to be consistent with the same 1990 baseline, the C02 inventory for the EU-15. 
1 The discussion is based on Member State trajectories, not applied to the inventory for the EU-15. Therefore there may be small discrepancies between the figures 
îentioned in the text and the figures provided in the box under Member State Trajectory above. 
H-2-
SPAIN 
1990 Emissions (GgC02) j Trajectory 1990/2000 on C02 
! inventory baseline (%) Effect of Measures (GgC02) 
Member State Trajectory (I) j 227300 ! 20.8 
Modified Trajectory j j 23 59470 
Target/Objective and Comments: Spain had initially forecasted a limited increase in emissions of 25% over 
1990 levels by 2000. This limited increase has been revised downwards to a band of 11-13% (2) 
Summary of measures: Measures focus on energy conservation and fuel switching. The conservation 
measures are mainly geared towards industry (burners, furnaces, more efficient technology), transport 
(technical and management measures), and residential/commercial sector (technical regulations, user 
awareness). Fuel switching measures include promotion of natural gas in industry (e.g. in cement and steel 
production as well as in combustion equipment), and in the residential sector (for space heating), as well as 
promotion of renewable energy (e.g. hydro and wind power) and CHP. Other measures include 
subsidisation of public transport, investment in rail infrastructure, and tax exemptions for gas oil used in rail 
transport. Measures to enhance sinks include afforestation, forest management, protection against forest 
fires, damage monitoring. 
Quantified Measures: None. 
Categorisation of Measures: The energy related measures are included in the Spanish National Energy Plan 
which runs from 1991-2000. Implementation of those measures has thus begun. The measures specified in 
the transport sector have been implemented. The measures to enhance sinks are under implementation. 
Projected C02 Emissions in 2000 Relative to Target/Objective (3): It is estimated that Spain will meet its 
objective for 2000, 25% increase over 1990 levels (4). As in the other cohesion countries, emission levels 
are more linked to economic growth than to the implementation of measures in the plan. Considering the 
low economic growth between 1990 and 1993 and depending on the level of economic growth in the 
coming years, it may even do somewhat better than limiting the emission increase to 25%. 
> Adjusted to be consistent with the same 1990 baseline, the C02 inventory for the EU-15. 
' Monitoring Mechanism Committee meeting, May 18, 1995. 
' The discussion is based on Member State trajectories, not applied to the inventory for the EU-15. Therefore there may be small discrepancies between the figures 
îentioned in the text and the figures provided in the box under Member State Trajectory above. 
> This objective has subsequently been revised downwards to a band of 11-13%. However, in the trajectories on this report, the figure 25% has been used. 
M3 
SWEDEN 
1990 Emissions (GgC02) j Trajectory 1990/2000 on C02 j Effect of Measures (GgC02) 
j inventory baseline (%) j 
Member State Trajectory (,) j 61300 j 4.4 ] 10200 
Modified Trajectory j j 6 j 
Target/Objective and Comments: Stabilisation at 1990 levels by 2000. 
Summary of measures: The focus of the C02 strategy is to switch from fossil fuels to renewable energy 
sources, improving energy management and more efficient use of energy. Measures to improve energy 
efficiency include technology procurement and demonstration of electricity efficient products, processes and 
systems in homes, non-housing premises and industry. Economic instruments play an important role in the 
strategy, e.g. C02 and energy taxes which have a cross-sectoral effect. Fuel taxation and R&D (alternative 
fuels and energy efficient vehicles) are the only measures that have been taken in the transport sector. In the 
forestry sector, measures include forest maintenance/management, and promotion of long-lived wood 
products. 
Quantified Measures: 
il. j Carbon taxes - energy sector. j 5.3 MtCOz j 
j 2. j Gasoline tax and carbon tax - transport sector. I 2.2 MtC02 j 
j 3. ; Efficiency programme. j 2.1 MtC02 j 
j 4. j Investment programme - biofuels. j 0.6 MtC02 i 
| 5. | Others. L.?;iM£°iI 
Ï TOTAL 10.4 MtCO, 
Categorisation of Measures: Majority of measures are under implementation. 
Projected C02 Emissions in 2000 Relative to Target/Objective (2): With present measures to combat climate 
change, total emissions of carbon dioxide are projected to increase slightly (eg 4 per cent) above 1990 levels 
in the year 2000. This projection is based on unadjusted data (non temperature corrected). If temperature 
adjustment is made for emissions in 1990 (3%) then stabilisation is achieved in 2000. This projection does 
not take account of energy and carbon tax increases which occurred in 1994. Considering that the majority 
of measures are in place, including a C02/energy tax, there is no reason to believe that Sweden cannot meet 
this projection. 
However, the forecast assumes that the phase-out of nuclear power is not initiated before 2000. Even if it is 
not begun immediately, it will be difficult to avoid meeting the increasing eneergy demand with fossil fuels. 
However, there is a large potential to increase biofuels in Sweden, especially in combined heat and power 
stations and for heating purposes (3). Once the nuclear phase-out is begun, CO, emissions from power 
generation will increase substantially. A final decision on the nuclear phase out has yet to be taken. 
"> This objective has subsequently been revised downwards to a band of 11-13%. However, in the trajectories of this report, the figure 25% has been used 
<2) The discussion is based on Member State trajectories, not applied to the inventory for the EU-15. Therefore there may be small discrepancies between the figures 
mentioned in the text and the figures provided in the box under Member State Trajectory above. 
1,1 According to the Act on Management on Natural Resources the remaining major rivers are protected to hydro power exploitation 
UNITED KINGDOM 
1990 Emissions (GgC02) j Trajectory 1990/2000 on C02 j Effect of Measures (GgC02) 
j inventory baseline (%) j 
Member State Trajectory (1) j 577000 j -6.1 j 71740 
Modified Trajectory j j -2 I 
Target/Objective and Comments: Stabilisation at 1990 levels in 2000. 
Summary of measures: Fuel switching and energy efficiency using economic instruments, regulations and 
information/education including: increased electricity generation from gas, CHP and renewables; 
establishment of the Energy Savings Trust to promote energy efficiency and conservation; increase in road 
fuel duties; introduction of VAT on domestic fuel and power; eco-labelling and energy labelling; revision 
of building standards. 
Quantified Measures (2). 
j 1. j Energy conservation in the home (VAT on domestic fuel use, ; 14664 GgC02 j 
j | new Energy Saving Trust, energy efficiency advice/information, j j 
; j eco-labelling, EC SAVE programme, revision of Building j j 
I j Regulations to strengthen energy efficiency requirements). j j 
I 2. j Energy consumption by business (energy efficiency ; 9165 GgC02 j 
j j advice/information, Energy Saving Trust schemes for small j ; 
j j businesses, Energy Design Advice Scheme, EC SAVE j ; 
j j programme, revision of Building Regulations to strengthen j j 
j j energy efficiency requirements). j j 
I 3. j Energy consumption in public sector (targets for central and j 3666 GgC02 j 
j i local government and public sector bodies). I j 
I 4. j Transport (increases in road fuel duties and commitment to real j 9165 GgC02 j 
! I increases of at least 5% on average in future budgets). j ! 
| TOTAL 36,660 GgCO? 
Categorisation of Measures: Most of the measures in place. However, many measures are voluntary or 
dependent on uncertain funding. 
Projected C02 Emissions in 2000 Relative to Target/Objective (3): The UK expects emission reductions as a 
result of the establishmentof an Energy Saving Trust. Due to changes in the anticipated level of funding, the 
contribution is now expected to be lower (at a minimum of 0.3 MtC, aquivalent to 1.1 MtC02) than 
originally estimated - although further schemes are being developed by the Trust which will contribute 
further savings. However, even taking into account the reduced contribution from the Energy Saving Trust, 
UK C02 emissions are now expected to be below 1990 levels, more as a result of fuel switching than of 
energy conservation. 
0> Adjusted to be consistent with the same 1990 baseline, the COz inventory for the EU-15. 
(2) The re-assessment of the contribution to be made by the Energy Saving Trust is not reflected in the table which is taken from the National Programme. 
(3) The discussion is based on Member State trajectories, not applied to the inventory for the EU-15. Therefore there may be small discrepancies between the figures 
mentioned in the text and the figures provided in the box under Member State Trajectory above. 
4-£ 

ISSN 0254-1475 
C0M(96) 91 final 
DOCUMENTS 
EN 14 
Catalogue number : CB-CO-96-096-EN-C 
ISBN 92-78-01226-2 
Office for Official Publications of the European Communities 
L-2985 Luxembourg