2002/149/: EFTA Surveillance Authority Decision No 149/02/COL of 26 July 2002 regarding environmental tax measures (Norway)
Date: 2002-07-26
Institutions: EFTA Surveillance Authority
Subjects: Norway, State aid, control of State aid, environmental protection, tax system

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EUROPEAN ECONOMIC AREA

EFTA SURVEILLANCE AUTHORITY

EFTA SURVEILLANCE AUTHORITY DECISION

No 149/02/COL

of 26 July 2002

regarding environmental tax measures

(Norway)

THE EFTA SURVEILLANCE AUTHORITY,

Having regard to the Agreement on the European Economic Area (1), in particular to Articles 61 to 63
thereof,

Having regard to the Agreement between the EFTA States on the establishment of a Surveillance Authority
and a Court of Justice (2), in particular to Article 24 and Article 1 of Protocol 3 thereof,

Having regard to the Procedural and Substantive Rules in the Field of State Aid (3), in particular Chapter 15
thereof (4),

Whereas:

Procedure

I. FACTS

By decision of 23 May 2001, the EFTA Surveillance Authority adopted new Environmental Guidelines (see
Decision No 152/01/COL). Pursuant to point 69 of these guidelines, the Authority proposed, as appro-
priate measures under Article 1(1) of Protocol 3 to the Surveillance and Court Agreement, that EFTA States
should bring their existing environmental aid schemes into line with these guidelines before 1 January
2002.

By letter from the Authority dated 23 May 2001 (Doc. No 01-3596-D), the Norwegian Government was
informed about the adoption of these new guidelines and asked to signify its agreement to the appropriate
measures. By letter from the Ministry of Trade and Industry dated 6 July 2001, received and registered by
the Authority on 10 July 2001 (Doc. No 01-5475-A), the Norwegian Government signified its agreement
to the appropriate measures.

The implementation of the new Environmental Guidelines was discussed between representatives from the
Authority and the Norwegian authorities on various occasions (i.e. at bilateral meetings in April, June and
September 2001).

(1) Hereinafter referred to as the ‘EEA Agreement’.
(2) Hereinafter referred to as the ‘Surveillance and Court Agreement’.
(3) Guidelines on the application and interpretation of Articles 61 and 62 of the EEA Agreement and Article 1 of
Protocol 3 to the Surveillance and Court Agreement, adopted and issued by the EFTA Surveillance Authority on 19
January 1994, published in OJ L 231, 3.9.1994; EEA Supplements No 32, 3.9.1994, last amended by the Authority's
Decision No 370/01/COL of 28 November 2001 (OJ C 34, 7.2.2002, p. 15); hereinafter referred to as the ‘Authori-
ty's State Aid Guidelines’.

(4) Chapter 15 of the Authority's State Aid Guidelines on Aid for Environmental Protection, as adopted by the Authori-
ty's Decision No 152/01/COL of 23 May 2001 (OJ L 237, 6.9.2001, p. 16), hereinafter referred to as the ‘Environ-
mental Guidelines’.

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By letter from the Ministry of Finance dated 31 January 2002, received and registered by the Authority on
5 February 2002 (Doc. No 02-1004-A), the Norwegian Government informed the Authority of the
measures in place and submitted its comments as regards compliance with the new Environmental Guide-
lines.

By letter dated 28 February 2002, the Authority acknowledged receipt of this letter (Doc. No: 02-1539-D).
The Authority emphasised that, having assessed the information submitted to it, the various schemes in
place could not be regarded as complying with the requirements laid down in the new Environmental
Guidelines. The Authority observed in this respect that the Norwegian Government had acknowledged this
fact and informed the Authority of plans to remedy the situation. However, the Authority took the view
that the plans and intentions referred to by the Norwegian Government were not sufficient, since they did
not contain any concrete proposals or commitments which would have ensured full compliance with the
new Environmental Guidelines as from 1 January 2002.

Having identified its main doubts concerning the compatibility of certain derogations from environmental
taxes with the Environmental Guidelines, the Authority requested the Norwegian Government to present
concrete proposals of adequate implementing measures and commitments ensuring that the requirements
set out in the new Environmental Guidelines were met from the prescribed date. In addition, the Norwe-
including a justification of the aid
gian Government was requested to submit additional
measures in question under the State aid rules. These proposals, commitments and additional information
were to reach the Authority within two months from receipt of the letter dated 28 February 2002.

information,

The Authority stressed that, in the absence of any concrete proposals, commitments and additional infor-
mation as requested by the Authority within that deadline, the Authority would proceed to open the
formal investigation procedure.

By letter from the Ministry of Finance dated 15 May 2002, received and registered by the Authority on 24
information. The
May 2002 (Doc. No 02-3995-A), the Norwegian Government submitted additional
Norwegian Government informed the Authority, inter alia, of the mandate of a working group which was
established in order to assess the consequences of the new Environmental Guidelines for the Norwegian
electricity tax system. This working group was asked to deliver a preliminary report by 1 July 2002.
Against this background, the Norwegian Government asked the Authority to allow for additional time in
order to comply with the requirements laid down in the new Environmental Guidelines.

By e-mail dated 5 July 2002, the Norwegian authorities sent the Authority a copy (in Norwegian) of a
preliminary report of the working group.

The Authority notes that it has not been formally informed by the Norwegian Government about that
report, nor has the Norwegian Government expressed its views on the conclusions presented in the report
or explained its further approach regarding the findings of the report. It should also be noted that this
report reached the Authority after the deadline for submitting information and proposals had expired. In
light of these circumstances, the Authority has not taken the content of this preliminary report into consid-
eration when assessing the various tax measures.

Description of aid measures

The following description is based partly on information provided by the Norwegian Government and
partly on information at the Authority's disposal.

The Authority regrets that the Norwegian Government has not submitted copies of the relevant legal provi-
sions governing the various tax measures at issue. Furthermore, the Authority observes that, even though
the Authority had specifically asked the Norwegian Government to submit supportive documents allowing
the Authority to verify the structure and logic of the Norwegian environmental tax system, including all
relevant background documents on the objectives pursued by the environmental taxes and the various
exemptions, no such information was provided by the Norwegian Government.

Tax on electricity consumption

The tax on electricity consumption was first introduced in 1971. According to the Norwegian Government
(see description given in letter of 31 January 2001), the objective of the tax was to ensure a more efficient
use of electric power and thus lead to positive environmental effects that would not otherwise occur.

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The tax covers all domestic use of electricity, subject to certain exemptions and, until 1993, reduced rates
for different industries. According to the Norwegian Government, these exemptions and reduced rates were
introduced to offset losses of competitiveness. In this respect, the Norwegian Government submitted data
on electricity consumption by the industries covered by the exemption and on increased costs for these
industries should the exemption from the electricity tax be abolished.

Since 1990, all users in Finnmark and seven municipalities in North Troms (Karlsøy, Kvænangen, Kåfjord,
Lyngen, Nordreisa, Skjervøy and Storfjord) have been exempted from the tax. This exemption applies to
both household consumption and all commercial activities.

Until 1992, the tax covered all industries, but certain sectors benefited from reduced rates (this was the
case for all or part of the power-intensive industry (1) as well as the pulp and paper industry). In 1993,
these industries were completely exempted. As from 1 January 1994, the exemption was extended to the
whole manufacturing industry, mining and greenhouse industry. According to the Norwegian Government,
the limitation of the exemption to power-intensive industries was abandoned, since the definition was
unclear and could not be maintained. From 1997, labour market enterprises that exercise industry produc-
tion are also exempted from the tax. Other sectors of industry are subject to the tax.

According to the Norwegian Government, the tax base was extended, as from 1 January 2001, to cover
the use of electricity in administration buildings in the manufacturing industry and mining enterprises.
According to the Norwegian Government, this amendment resulted in a situation where only electricity
used in production processes was exempted from the tax. In order to be defined as an administration
building a minimum of 80 % of the building's space has to be used for administration purposes. This
meant that if production activities occupied above 20 % of the space, the electricity delivered to that
building was not to be taxed. This was, according to the Norwegian Government, seen as the only practical
definition.

According to the Norwegian Government, the existing exemptions from the tax (i.e. sectoral and regional
derogations) cover about 45 % of the total electricity consumption and about 70 % of electricity consump-
tion in all industries in Norway.

The following table gives an overview of the applicable tax rates and exemptions since 1993, based on
figures submitted by the Norwegian Government.

Table 1: Electricity tax in øre per kWh (expressed in 2002-prices)

1993

Tax rate

5,60

1994

6,12

1995

6,09

1996

6,14

1997

6,34

1998

6,34

1999

6,41

2000

8,95

2001

11,47

2002

9,30

Reduced rate

2,80 (1)

- (2)

—

—

—

—

—

—

—

As in
1994

As in
1994

Exemptions

Manufac-
turing
industry
and
mining
exempted

Power-
intensive
industry,
pulp and
paper
industry
and green-
houses

As in
1997

As in
1997 (3)

As in
1999

As in
1999 but
excluding
electric
power
used in
adminis-
trative
buildings
from
exemption

Exemption
was
extended
so as to
include
labour
market
companies
under-
taking
industry
produc-
tion

(1) The Norwegian Government pointed out that the manufacturing industry and mining paid only 2,3 øre per kWh.
(2) The manufacturing industry and mining were, as from 1 January 1994 fully exempted from the tax.
(3) However, according to the Norwegian Government, the exemption for users with electric boilers was abolished.

(1) The main sectors of the power-intensive industry are the aluminium and ferro alloy industries.

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In addition, the Norwegian Government submitted information on the revenues and calculated tax expendi-
tures under the tax on electricity consumption. Tax expenditure is calculated as revenue forgone by the
State due to the tax exemptions of tax reductions. For the purpose of these calculations, possible beha-
vioural changes caused by an abolishment of the tax exemption are not taken into account.

Table 2: Tax on electricity consumption: Revenues and tax expenditures expressed in million NOK

Revenues

1999

3 267

2000

4 205

2001

6 530

2002

6 206

Tax expenditure due to sectoral exemptions

2 735

3 940

5 595

4 605

Tax expenditure due to regional exemption

100

140

190

160

The Authority notes that the relevant legal provisions governing the electricity tax would seem to stipulate
as a general rule that all domestic consumption of electricity is liable to taxation (1). On the other hand, the
relevant provisions formulate exemptions for certain industries or regions (2). The sectoral derogations are
defined with reference to their statistical classification.

In some cases, the scope of the exemption has been further clarified/limited, so that electricity used on
administrative buildings would not be covered by the exemption (3).

CO2 tax

The CO2 tax on mineral oil and petrol was introduced in 1991 and on coal and coke in 1992. When the
tax was first introduced, it was an integrated element of the existing excise tax-systems on mineral oil,
petrol and coal and coke. As part of the green tax reform in 1999, the CO2 tax was proposed as a separate
tax in the legislation. The rate of the CO2 tax on mineral oil was set at NOK 0,490 per litre (4). The rate of
the CO2 tax on coal and coke was increased, in the period between 1994 and 2002, from (2002) NOK
0,410 to (2002) NOK 0,490 per kg.

The tax levied on coal and coke covers products used for energy purposes. According to the Norwegian
Government, the use of coal and coke as raw materials or as reducing agents in industrial processes is
exempted from the CO2 tax. This exemption was adopted in 1992 when the CO2 tax on coal and coke was
introduced. According to the Norwegian Government, coal and coke are used as raw materials or reducing
agents in the production of carbides, ferro alloys and primary aluminium and magnesium. These industries
were also energy-intensive and would not be viable without the exemption. In its letter dated 31 January
2002, the Norwegian Government stated that the reason for the exemption was that available techniques
were based on the use of carbon material and that the producers in question were exposed to international
competition.

Furthermore, the CO2-tax is not levied on coal and coke used for energy purposes in production of cement
and leca. This exemption was established in 1992, as the tax came into force. The reason for this exemp-
tion is, according to the Norwegian Government, that possible large-scale substitutes to coal and coke
would be unprofitable and that the industry concerned would be exposed to international competition.

The paper and pulp industry has paid a reduced rate of NOK 0,245 per litre since January 1993.

(1) See the Norwegian Parliament's decision on the electricity tax in the context of the State Budget for 2002, Vedtak
om forbruksavgift på elektrisk kraft, 28 November 2001, paragraph 1 as well as Chapter 3 of the Regulation on
Excise Duties, paragraph 3.12.1.

(2) See the Norwegian Parliament's decision on the electricity tax in the context of the State Budget for 2002, Vedtak
om forbruksavgift på elektrisk kraft, 28 November 2001, paragraph 1 as well as Chapter 3 of the Regulation on
Excise Duties, paragraph 3.12.4.

(3) Chapter 3 of the Regulation on Excise Duties, paragraph 3.12.5.
(4) According to information submitted by the Norwegian Government, the rate expressed in 2002 NOK has not

changed since 1994.

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The Norwegian Government has submitted information regarding revenues and tax expenditures under the
CO2 tax (1).

Table 3: CO2 tax revenues and tax expenditures in million NOK (1)

Revenues

1999

6 904

2000

6 567

2001

6 600

2002

7 018

Tax expenditure

2 125

2 175

2 230

2 270

(1) The Norwegian Government explained that the figures were calculated using the CO2 tax on mineral oil at a rate of NOK 0,49 per

litre as a benchmark.

The Authority notes that based on the relevant legal provisions governing the CO2 tax, certain uses of the
taxable products are exempted from the tax. Pursuant to paragraph 3.6.3 of Chapter 3 of the Regulation
on Excise duties, products used as raw material are eligible for refund of the tax to the extent that CO2
emissions into the air are less than the carbon content of the respective product would indicate. According
to paragraph 3.6.4 of Chapter 3 of the Regulation on Excise Duties, coal and coke used as reducing agents
are exempted from the tax. The exemption covers only the amount of the products necessary for the
reduction process. Furthermore, coal and coke used for the manufacture of clinker in combination with
the production of cement and leca are exempted from the tax.

In addition, the Customs and Excise Duties Department issued explanatory notes to the exemptions
referred to above which can further illustrate the background for the exemptions at issue (2).

As regards the use of coal and coke as raw materials for industrial processes, the notes say that when coal
and coke are a part of the finished product, either permanent or temporary, in a way that implies no emis-
sions of CO2, or that the emissions are lower than if it had been a normal combustion, the use of coal and
coke is exempted from tax. This is the case if coal and coke are used, inter alia, as raw materials for produc-
tion of graphite electrodes and electrode mass and e.g. by production of calcium carbide.

As regards the use of coal and coke as reducing agents in industrial processes, the notes state that in some
cases, coal and coke are a necessary part of the chemical process, but will not be included as a part of the
finished product. In such cases the level of CO2 emissions is comparable to emissions from use of coal and
coke for energy purposes. The reason for the exemption is said to be that there are no alternative materials
for such processes other than coal and coke.

The Norwegian Government submitted figures about the CO2 emissions caused by the various industries as
well as estimates regarding the costs due to the CO2 tax.

SO2 tax

In 1970, a tax on mineral oil was introduced. The Norwegian Government explained that, pursuant to
Regulation of 17 September 1976 No 2 (3), all or part of that tax could be reimbursed on application, if
the emission from the use of the product was less than the content of sulphur would indicate. All users of
mineral oil were eligible to apply for reimbursement. This showed, according to the Norwegian Govern-
ment, that the SO2 tax targets in fact the sulphur dioxide actually emitted.

(1) As regards the concept of ‘tax expenditure’, see explanation above.
(2) Toll- og avgiftsdirektoratets kommentarer Fritak for industriell bruk, kull og koks (jf. Stortingets vedtak om co2-avgift

§ 3 nr.1 bokstav d og § 3 nr.4 bokstav a, jf. forskriften §§ 3-6-3 og 3-6-4).

(3) The Authority notes that this Regulation was not submitted to it.

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As from 1993, the tax was based on the content of sulphur in the oil and increased according to the
percentage of the content of sulphur. The tax base covered petroleum, gas oil, solar oil, auto diesel, diesel
oil and fuel oil or any oil that might be used as fuel oil. In 1999, the sulphur-based tax levied on mineral
oil was changed into a SO2 tax.

At the same time, the tax base was extended so as to include coal and coke. However, SO2 emissions due
to the use of coal and coke were taxed at a reduced rate. The Regulation on sulphur tax on mineral
products of 18 December 1998 No 961 (1) provided for the application of a differentiated tax depending
on the different categories of coal and coke, based on the presumed sulphur content. Following the exten-
sion of the scope of the SO2 tax, the reimbursement scheme under Regulation of 17 September 1976 No
2 (see above) was extended so as to cover also the new products subject to the tax.

The scope of the tax was further extended in 1999, so as to include also SO2 emissions from oil refinery
plants. In order to avoid possible double taxation, the Regulation on sulphur tax on mineral products of
18 December 1998 No 961 paragraph 1, No 3 was implemented. This provision stipulated that if products
already taxed caused the emission covered by the tax, the former tax should be deducted from the tax
payable on the emission. Hence, as far as the oil refineries used mineral oil in the refinery process the
amendment in 1999 was in reality merely a technical one. From being taxed on emission indirectly
through the reimbursement scheme, the tax was formed directly as an emission tax. Oil refineries were
thus singled out as a candidate where it was considered as more efficient to apply the SO2 tax directly on
the emission from the refinery. In the Norwegian Government's view, only as far as the emissions were
caused by sources not previously taxed, the emission tax on oil refineries could be said to represent a ‘new’
tax. Because oil refineries use raw oil to produce mineral oil products, there is emission from this process
as such. Raw oil is, however, not taxed as a product and thus not part of the reimbursement scheme.

According to the figures presented by the Norwegian Government, the basic SO2 tax rate on mineral oil
decreased from (2002) NOK 0,084 per litre in 1994 to (2002) NOK 0,070 per litre in 2002. The rate of
the SO2 tax in coal and coke and oil refineries decreased from (2002) NOK 3,24 per kg SO2 in 1999 to
(2002) NOK 3,14 per kg in 2002.

As from 1 January 2002, the SO2 tax on use of coal and coke and on oil refineries was abolished. The
Norwegian Government explained that the industry, which was previously covered by the SO2 tax, would
instead be regulated through emissions permits in accordance with the Pollution Control Act. According to
the Norwegian Government, the abolishment of the tax is to be seen against the background of the Norwe-
gian States commitments under the 1999 Gothenburg Protocol, which sets a ceiling on Norwegian SO2
emissions of 22 000 tonnes in 2010. The Norwegian Government explained that in order to achieve that
emission limit, Norwegian SO2 emissions would have to decrease by 7 000 tonnes. Calculations made by
the Norwegian State Pollution Control Authority showed that this reduction was best made by the process
industry. To this end, a letter of intent was signed, on 19 September 2001, between the Ministry of Envir-
onment and the Norwegian Federation of Norwegian Process Industries (PIL), on behalf of undertakings in
the following sectors: oil refineries, chemical/ceramic materials, cement, ferro alloys and aluminium.

The Norwegian Government stated that in the environmental field there are different kinds of instruments
or measures that should be considered in order to choose the most efficient one to reach the target set, the
tax instrument being one of them. In St.prp. No 54 (1997-1998), several measures were considered in
order to reduce the overall emission of SO2, and it was chosen to implement a tax on the use of coal and
coke with a reduced rate. However, a study published by the Norwegian Pollution Control Authority
showed that only minor emission reduction could be achieved by this reduced rate. Hence, the tax was
abolished and other measures, such as the Agreement of Intent entered into with PIL, were introduced.

(1) The Authority notes that this Regulation was not submitted to it.

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According to the Agreement of Intent, the Federation of Norwegian Process Industries declares on behalf
of the companies listed in an Appendix to the Agreement (1), that they would develop technology and build
cleansing plants that will reduce Norway's emission of SO2 by a minimum of 5 000 tonnes. Furthermore,
PIL will make concrete proposals on how such an emission reduction may be carried out and at the same
time make proposals on how a total reduction of 7 000 tonnes may be achieved.

The Agreement further stipulates that emissions from individual operations will be regulated by the Norwe-
gian Pollution Control Authority (SFT) through licences in accordance with the Pollution Act associated
with implementation of the EC Directive on integrated pollution control (the IPPC Directive) for existing
industry which is to be operated in accordance with the Directive's requirements by 30 October 2007. To
the extent permitted by the Pollution Act, the environmental protection authorities aim to design the emis-
sion licences in such a way that the industry is given the opportunity to meet the reduction requirements
by cooperating in taking joint emission reducing measures where the industry finds this most efficacious.
The emission licences are also to provide rules on the more detailed terms for joint implementation,
including that the requirements in the IPPC Directive on use of BAT (2)
in the individual plants are
complied with. Furthermore, the emission licences are to be formulated in accordance with the require-
ments for alternative methods for relief from duty in the EFTA Surveillance Authority's guidelines for envir-
onmental support.

According to the Agreement of Intent, PIL is to put forward proposals for methodology to calculate/
measure the emission of SO2 from individual companies by 1 June 2002.

The Norwegian Government declared that it had the intention for regulation, in accordance with the Pollu-
tion Act, to be the main tool to reduce the SO2 emissions from industrial processes until the deadline for
emission reduction measures has been reached, at the latest by 2010. The legally binding obligations will
thus be contained in the companies' licences. Accordingly, the Government undertook to put forward a
proposal to the Norwegian Parliament that the duty on emission of SO2 from use of coal and coke and
from the refineries be removed from 1 January 2002.

It is finally stated that the Agreement with PIL is to be regarded as an agreement of intent that does not
bind the parties legally. The Norwegian authorities also made a proviso that this agreement was in line
with the EFTA Surveillance Authority's guidelines for environmental support.

With a view to implementing the agreement of intent, PIL has established a so-called process industries'
environment fund'. The fund is organised as an independent trust. Each individual participating company
has apparently signed an implementation agreement with the fund. The most important element in the
implementation agreement is that the companies undertake to pay a sum to the fund that corresponds to
the current SO2 tax. The fund's resources will be used to finance cleansing plants prioritised according to
the costs until the agreement of intent target is reached.

Based on the figures provided by the Norwegian Government, the following table gives an overview of
revenues and tax expenditures (3) under the SO2 tax.

Table 4: SO2 tax revenues and expenditure in million NOK

Revenues

Tax expenditure

1999

344

540

2000

117

525

2001

140

540

2002

98

600

(1) The sectors enumerated in the Appendix are: oil refineries, chemical/ceramic materials, cement, ferro alloys and

aluminium.

(2) ‘Best available techniques’ (BAT).
(3) For an explanation of the concept of tax expenditures, see above.

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The Norwegian Government also provided information on the SO2 emissions caused by the use of coal
and coke and oil refineries as well as estimates regarding costs due to the SO2 tax.

II. APPRECIATION

Scope of the present decision

The Authority points out that the present decision is limited to assessing whether the Norwegian Govern-
ment complied with its obligations stemming from the appropriate measures proposed by the Authority
and accepted by the Norwegian Government. Consequently, the current investigation only concerns the
examination of compatibility under Article 61(3)(c) of the EEA Agreement in combination with the new
Environmental Guidelines of aid schemes covering the period as from 1 January 2002.

The present investigation covers only aid measures in the form of exemptions from the electricity tax,
derogations from the CO2 tax as well as through the partial abolishment of the SO2 tax. With respect to
other measures which were communicated by the Norwegian Government in its letter dated 31 January
2002, the Authority reserves the right to assess these measures at a later stage.

State aid within the meaning of Article 61(1) of the EEA Agreement

The Norwegian Government claimed in its letter dated 15 May 2002 that, contrary to the views expressed
in the letter dated 31 January 2002, certain of the measures in question could be regarded as falling outside
the scope of Article 61(1) of the EEA Agreement. The Authority was invited to review these measures
against the background of the Norwegian Government's interpretation of the concept of State aid with
respect to environmental taxes.

The Norwegian Government claimed that it would result from the EC Commission's practice (1) and case
law from the European Court of Justice (2) that it is within the EEA State's discretion to decide which
products to be taxed and what particular use of certain products should be taxed. The Norwegian Govern-
ment takes the view that measures which are restricted to a particular input factor or to a particular use of
certain products, or a particular conduct, are general in nature. Such measures would not favour certain
undertakings or the production of certain goods. As regards a possible justification of the measures, in light
of the objectives pursued by the measures in question, the Norwegian Government makes reference to case
law and the Commission's proposal for a Council Directive restructuring the Community framework for
the taxation of energy products which illustrated circumstances in which favourable tax treatment was
regarded as being justified by the nature and general scheme of the tax system at issue (3).

(1) In the respect, the Norwegian Government referred, in particular, to the Commission's Decision of 3 April 2002
regarding the dual-use exemption from the climate change levy in the United Kingdom (State aid No C 18/2001 and
C 19/2001) as well as the Commission's Decision regarding the electricity reform in Denmark (State aid N 416/99).
(2) In this respect, the Norwegian Government referred to the following cases: Judgment of the European Court of Justice
of 2 July 1974, Case 173/73, Italy v. Commission [1974] ECR 709, Judgment of the European Court of Justice of 2
February 1988, Joined cases 67, 68 and 70/85, van der Kooy v. Commission [1988] ECR 219, Judgment of the
European Court of Justice of 17 June 1999, Case C-75/97, Belgium v. Commission (Maribel bis/ter) [1999] ECR I-
3671 and Judgment of the European Court of Justice of 8 November 2001, Case C-143/99, Adria Wien Pipeline.
(3) In addition to the case law referred to above, the Norwegian Government mentioned the judgment of the European

Court of Justice of 22 November 2001, Case C-53/00, Ferring.

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By virtue of Article 61(1) of the EEA Agreement, ‘any aid granted by EC Member States, EFTA States or
through State resources in any form whatsoever which distorts or threatens to distort competition by
favouring certain undertakings or the production of certain goods shall, in so far as it affects trade between
the Contracting Parties, be incompatible with the functioning of this Agreement.’

State aid within the meaning of Article 61(1) of the EEA Agreement covers ‘…measures which, in various
forms, mitigate the charges which are normally included in the budget of an undertaking and which,
without therefore being subsidies in the strict meaning of the word, are similar in character and have the
same effects …’ (1).

Consequently, a system under which the public authorities grant to certain undertakings a tax exemption
that relieves them of some of their costs and confers on them financial advantages which improve their
competitive position constitutes State aid within the meaning of Article 61(1) of the EEA Agreement if the
aid is capable of affecting trade between the Contracting Parties and distorting competition.

The introduction of environmental taxes is not as such caught by Article 61(1) of the EEA Agreement,
insofar as they are general measures which do not favour particular firms or sectors of industry (2). Excep-
tions to a general tax do, however, fall under that provision, if they are targeted at certain firms or sectors
of industry, and without these exemptions being justified by the nature or general scheme of the tax system
in question (3).

As a first step, and when assessing whether or not a measure is targeted at certain firms or sectors of indus-
tries, both the legal provisions governing the tax measure in question and its effects have to be taken into
account (4). Therefore, a measure may be selective if the legal provisions explicitly limit the tax benefits to
certain sectors of the industry. In the absence of such explicit provisions, the measure may still be selective
if the application of certain criteria laid down in the tax provisions or the definition of the scope of the tax
measures in question results in only certain, clearly identifiable, sectors of industry actually benefiting from
favourable tax treatment.

The assessment of whether or not certain measures constitute exemptions or derogations from a general
rule/common system takes, as a starting point, the structure of a given tax measure: based on the legal
provisions governing the tax measures in question, it needs to be determined whether there are general
rules from which exceptions are granted (5). However, it should be stressed that the denomination of the
measures in question is not decisive (6). For the qualification as a derogation it is not determining whether
a specific measure is designed as an exemption or as a limitation of the scope of the measure. What needs
to be assessed is whether the measure at issue constitutes a derogation, by virtue of its actual nature, from
the general system in which it is set (7). This assessment needs to be based on the objectives pursued by the
measures at issue.

(1) Judgment of The European Court of Justice of 17 June 1999, Case C-75/97, Belgium v. Commission, (Maribel bis/ter)

[1999] ECR I-3671, paragraph 23.

(2) See point 17B.3.1.(1) of Chapter 17 B of the Authority's State Aid Guidelines on the application of State aid rules to

measures relating to direct business taxation.

(3) See point 17B.3.1.(4) of Chapter 17B of the Authority's State Aid Guidelines; see also Judgment of the European

Court of Justice of 2 July 1974, Case 173/73, Italy v. Commission [1974] ECR 709, paragraph 15.

(4) In this respect, it should be emphasised that Article 61(1) of the EEA Agreement ‘…does not distinguish between
measures of State intervention by reference to their causes or their aims but defines them in relation to their effects’;
‘Maribel bis/ter’, paragraph 25; see also Judgment of the European Court of Justice of 29 February 1996,Case C-56/
93, Belgium v. Commission [1996] ECR I-723, paragraph 79.

(5) See point 17B.3.1.(4) of Chapter 17B of the Authority's State Aid Guidelines.
(6) See Opinion of Mr Advocate General Ruiz-Jarabo Colomer delivered on 17 September 1998, Case C-6/97, Italian
Republic v. Commission [1999] ECR I-2981, paragraph 27 footnote 17: ‘What matters is not the formal name given
to the measure (exemption, reduction, bonus, deduction,relief etc.) but its nature as a fiscal provision creating an
exceptional situation in favour of one or more taxable persons.’

(7) See Opinion of Advocate General Darmon delivered on 17 March 1992, Joined Cases C-72 and 73/91 [1993] ECR I-

887, paragraph 50.

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The Authority recalls that the European Court of Justice held in the Adria Wien case that, when assessing
whether or not State aid rules are applicable, ‘the only question to be determined is whether, under a parti-
cular statutory scheme, a State measure is such as to favour 'certain undertakings or the production of
certain goods within the meaning of Article 92(1) of the Treaty in comparison with other undertakings
which are in a legal and factual situation that is comparable in the light of the objective pursued by the
measure in question’ (1).

As a second step, it has to be ascertained whether there is a ‘justification for this exemption on the basis of
the nature or general scheme of this system’ (2). When assessing a possible justification with respect to
environmental tax measures, special attention must be paid to the environmental policy considerations
underlying the national legislation at issue and it needs to be examined whether, having these considera-
tions in mind, a different treatment of economic operators is justified or whether undertakings/sectors
benefiting from the tax advantages are equally contributing to the negative environmental effects the tax in
question was designed to penalise (3).

Finally, the Authority would like to point out that it is, in principle, for the EFTA State concerned to design
its environmental tax systems as it sees fit. This includes the EFTA State's freedom to decide which
products and activities should be brought within the scope of a specific environmental tax system.
However, in exercising its freedom to determine the national environmental tax system, the EFTA State
concerned has to ensure that, in order not to be in conflict with the EEA State aid rules, measures which
are benefiting certain sectors of industry are in line with the environmental objectives underlying the tax
measures in question. It is for the Government concerned to present information allowing the Authority to
verify that the favourable tax measures adopted can be regarded as an implementation of the objectives
inherent to the tax system in question.

It is against this background that the Authority assessed the various tax measures.

Electricity tax

According to the Norwegian Government, as from 1 January 2001, the preferential tax measure in ques-
tion could not be regarded as an exemption from the electricity tax system directed to a particular sector
of the economy (manufacturing and mining sector), as opposed to e.g. the service sector. The tax would
have to be regarded as a tax that is limited in scope covering all use of electricity other than electricity used
for production purposes.

The Norwegian Government took the view that the distinction depending on the specific use of electricity
as opposed to a distinction according to specific sectors of industry could not be regarded as constituting
aid.

Based on the relevant rules, as laid down in the Regulation on Excise Duties (Chapter 3) as described above,
the Authority takes the view that the system governing the electricity tax is currently designed in such a
way that the general rule is that all consumption of electricity is liable to taxation. The Norwegian Govern-
ment's argument that the general rule underlying the current electricity tax system would be that only elec-
tricity used for purposes other than production processes would be liable to taxation does not seem to find
support in the relevant rules referred to above. These rules clearly establish that certain industries, defined
by reference to their classification by the Central Bureau of Statistics of Norway, shall be exempt from the
tax. This definition of the scope of the exemption results in certain sectors of industry not benefiting from
the exemption although it may not be excluded that also within these sectors electricity is used for produc-
tion processes.

It results clearly from the relevant case law that exemptions defined by reference to specific sectors are to
be regarded as selective measures which cannot, in principle, be justified by the nature or logic of the tax
system in question (4).

(1) Judgment of the European Court of Justice of 8 November 2001, Case C-143/99, Adria Wien Pipeline [2001] ECR I-

8365, paragraph 41.

(2) Judgment of the European Court of Justice of 2 July 1974, Italy v. Commission, Case 173/73 [1974] ECR 709, para-

graph 15.

(3) See Judgment of the Court of Justice of 22 November 2001, Case C-53/00, Ferring SA v. Agence centrale des orga-

nismes de sécurité sociale (ACOSS) [2001] ECR I-9067, paragraphs 17 to 22.

(4) In the Adria Wien-judgment, the European Court of Justice held that ‘…any justification for the grant of advantages
to undertakings whose activity consists primarily in the production of goods is not to be found in the nature or
general scheme of the taxation system…’, paragraph 49. Furthermore, in the Maribel-case, the Court held ‘that the
limitation of the increased reductions to certain sectors rendered those reduction measures selective, so that they
fulfilled the condition of specificity.’, paragraphs 28 to 31.

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In addition, the Authority is not convinced that the exemptions could be regarded as reflecting the Norwe-
gian Government's choice to impose a tax only on certain kinds of consumption of electricity. As the
Norwegian Government has stated itself (see letter dated 31 January 2002), the exemptions for various
industries were introduced to offset losses of competitiveness. The Authority also notes that the Norwegian
Government has not explained how the limitation of the exemption to the effect that electricity used in
administrative buildings would be subject to the tax actually ensures that only electricity used for produc-
tion processes would benefit from the tax exemption. In this respect, the Authority notes in particular that
the Norwegian Government has not given any definition of what would be regarded as production
processes and administrative purposes. Furthermore, the Authority has doubts whether it would be in line
with the objectives purportedly pursued by the electricity tax, namely to reduce electricity consumption, to
exclude the use of electricity for certain purposes, such as the use of electricity for production processes as
opposed to other uses.

Finally, it is also clear from case law that the regionally differentiated application of tax measures consti-
tutes a selective measure caught by Article 61(1) of the EEA Agreement (1).

In light of the above considerations, and based on the information in the Authority's possession, the
Authority has concluded that the exemptions from the electricity tax for certain industries and regions, as
laid down in paragraph 3.1.4 of Chapter 3 of the Regulation on Excise Duties, could constitute a selective
measure which seems to derogate from the general system of taxation on consumption of electricity.

These derogations confer a financial benefit to undertakings covered by the exemptions, since these compa-
nies are relieved of charges that would normally be borne from their budgets. This advantage is granted
through State resources as the State suffers a loss of State revenues. Based on the figures provided by the
Norwegian authorities, the loss in tax revenues due to the sectoral and regional exemptions for 2002 was
estimated to amount to NOK 4 605 million and NOK 160 million, respectively (2). The recipient firms
exercise an economic activity on markets on which there is or could be trade between the Contracting
Parties or on which firms from other EEA countries might wish to establish themselves. The exemptions
therefore distort or threaten to distort competition and could affect trade between the Contracting Parties.

Consequently, the derogations from the electricity tax for certain industries and regions could be regarded
as constituting aid within the meaning of Article 61(1) of the EEA Agreement.

CO2 tax

Derogation for coal and coke used as raw materials or reducing agents

The Norwegian Government took the view that the derogations from the CO2 tax for coal and coke used
as raw materials and for coal and coke used as reducing agents could fall outside the scope of Article 61(1)
of the EEA Agreement.

The Norwegian Government claimed that both derogations were defined by a particular use of the
products in question and not as an exemption/reduction directed to certain undertakings or for the produc-
tion of certain goods. This derogation was open for all undertakings that use coal and coke for this
purpose. In such a situation, the Norwegian Government took the view that the tax exemption for certain
uses of the products could only be regarded as ‘selective’ if certain undertakings would not benefit from the
tax exemption even though they would also use the products for the purposes described in the exemption
clause.

In the alternative, the Norwegian Government claimed that, at least the derogation for the use of coal and
coke as raw materials could be justified by the underlying principle actually pursued.

(1) EFTA Court judgment 20 July 1999 regarding the Norwegian regionally differentiated social security tax, Case E-6/

98, The Government of Norway v. EFTA Surveillance Authority [1999] Report of the EFTA Court, p. 74.

(2) According to the Norwegian Government, these figures were taken from Budsjettinnstilling S. nr. 1 (2001-2002).

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The Norwegian Government claimed that the objective of the CO2 tax was the reduction of CO2 emissions.
The tax was levied on mineral oil products used for energy purposes. To the extent that certain uses of
mineral oil products other than for energy purposes do not result in CO2 emissions, the exemptions/
refunds could be regarded as justified by the logic of the measure in question.

In this respect, the Norwegian Government stated that processing coal and coke into the end product
caused no or negligible emission of CO2. The expressed reason for this is either the ‘low’ temperature
(4 500 °C) or the lack of oxygen in this process. As the purpose of the tax is to target the emission of CO2,
the derogation for the use of coal and coke as raw materials was, in the Norwegian Government's view,
justified by the underlying objective actually pursued.

In the Norwegian Government's view, the underlying objective for introducing a tax on the use of coal and
coke was in part to reduce the use of these products for energy purposes, and in part to avoid the risk of
conversion from use of mineral oil, that was already taxed, to the use of the not taxed coal and coke.
Taking these objectives into account, the Norwegian Government claimed that the derogation for the use
of coal and coke as raw materials and reducing agents, which are not used for energy purposes, could be
regarded as justified. Furthermore, the Norwegian Government argued that as it did not see any alternative
products that could be used in this particular process, both derogations could be said to be justified also
on these grounds.

The Authority observes that the refund possibility for coal and coke used as raw materials as well as the
exemption for coal and coke used as reducing agents are not defined with respect to a specific sector of
the industry. However, it would seem that coal and coke are only used for the specified purposes in parti-
cular industries. Consequently, the exemptions limited to these purposes would appear to necessarily
benefit only these industries. In addition, the Authority observes that the Norwegian Government itself
seems to regard these exemptions as being targeted at specific industries, namely in the production of
carbides, ferro alloys and primary aluminium and magnesium and states that these industries would not be
viable without the exemption (1).

The Authority does not exclude at this stage that certain exemptions/reductions may be regarded as justi-
fied where it can be demonstrated that certain uses of the taxable product in question do not contribute to
the negative environmental effects that the tax in question seeks to penalise.

The Authority notes, however, that the Norwegian Government has not submitted verifiable information
on CO2 emissions from the use of coal and coke as raw materials in the different industries covered by the
exemption. Furthermore, the Norwegian Government has not explained how the refund mechanism estab-
lished under paragraph 3.6.3(1) of Chapter 3 of the Regulation on excise duties is applied in practice.
Consequently, the Authority was not in a position to ascertain that the exemption is applied in a way that
would limit the exemption to processes not causing CO2 emissions.

As regards the exemptions from the CO2 tax for coal and coke used as reducing agents (see paragraph
3.6.4 of Chapter 3 of the Regulation on excise duties), the Authority notes that, according to the explana-
tory notes issued by the Customs and Excise Duties Directorate, the use of coal and coke as necessary parts
of the chemical process results in emission of CO2 at a similar level compared to emissions from use of
coal and coke for energy purposes. Consequently, the exemption would seem to be in contradiction to the
objectives of the CO2 tax, namely to impose a levy on products causing CO2 emissions. According to the
Norwegian Government, the reason for the exemption was that there were no alternative materials for such
processes other than coal and coke.

In this respect, the Authority notes that the Norwegian Government has not submitted any further infor-
mation which would have enabled the Authority to verify that those industries benefiting from the exemp-
tion are actually in a situation where it could be said that there were no alternative materials for the indus-
trial processes in question. Furthermore, the Norwegian Government has not explained why in such
circumstances CO2 taxes should not be levied.

It results from the Environmental Guidelines that aid measures in relation to environmental taxes must take
into account the basic principles of environmental policy objectives when assessing their compatibility
under the EEA State aid rules. The basic principles, as referred to in the guidelines are the ‘polluter pays’
principle. Accordingly, and pursuant to point 19 of the guidelines,
‘…aid should no longer be used to
make up for the absence of cost internalisation. If environmental requirements are to be taken into account
in the long term, prices must accurately reflect costs and environmental protection costs must be fully
internalised.’

(1) The Authority also takes note of the Norwegian Government's paper on Climate Change Policy, where in Table 2
reference is made to ‘sectors exempt from taxation: …coal and coke for processing purposes (iron alloy, carbide and
aluminium industry)’ (underlined here).

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In light of the foregoing considerations, the Authority has doubts that the refund of the CO2 tax regarding
coal and coke used as raw materials and the exemption regarding coal and coke used as reducing agents
can be justified by the nature and logic of the tax system at issue. In addition, the Authority notes that the
Norwegian Government stated in its letter dated 31 January 2002, that the industries benefiting from the
exemptions were energy-intensive industries which were exposed to international competition and would
not be viable without the exemptions. This seems to indicate that the underlying reason for the exemptions
are not inherent to the tax system at issue.

Exemption for the use of coal and coke for energy purposes in the manufacture of cement and leca

According to the Norwegian Government, the reason for exempting the use of coal and coke for energy
purposes in the manufacture of cement and leca was partly that large-scale substitutes for coal and coke
would be unprofitable, and partly that the industry was exposed to international competition. The former
might indicate, according to the Norwegian Government, that the amount of the energy product required
would be decided by the manufacturing process, and that only substitution and not reduction of the use of
coke was an alternative. As far as this was the case, the Norwegian Government argued that it would seem
to result from the EC Commission's decision in the dual-use case that the limited scope for a producer to
change the type and amount of the energy product required for the process would have to be taken into
account. However, the Norwegian Government recognised that the exemption for the manufacture of
cement and leca might require further assessment. The Norwegian Government therefore informed the
Authority that this exemption would be assessed in more detail with the State Budget for 2003.

The Authority notes that this exemption is limited to a specific sector of industry and is also contrary to
the general rule established under the CO2 tax system that all uses of coal and coke for energy purposes
should be subject to tax. The exemption is therefore a sector-specific measure and cannot, in principle, be
justified by the nature or logic of the tax system in question (1). In this respect, the Authority notes that the
Norwegian Government has not demonstrated that it would only be the cement industry which required a
special treatment in light of the alleged problems of not having access to substitutes for coal and coke.
Furthermore, and as stated above (2), even if it should result that there are no alternative products to be
used by the cement industry, this does not in itself justify a derogation from the rules, to the extent that
such a derogation runs counter to the environmental objectives actually pursued.

The Authority concludes that the Norwegian Government has not submitted sufficient information demon-
strating that the exemptions in question could be regarded as being justified by the nature and general
scheme of the CO2 tax system.

The Authority is aware of the EC Commission's decision regarding the dual-use case in the United
Kingdom (3) as well as the EC Commission's proposal regarding a new framework for energy taxation
within the European Union (4). The Authority does not exclude that the considerations underlying the EC
Commission's assessment may be of relevance for the exemptions from the CO2 tax on coal and coke used
as raw materials or reducing agents. However, the Authority would like to point out that the objectives
pursued by the EC Commission's proposal on energy taxation, and which, according to the EC Commis-
sion, justified certain exemptions from the tax concerned, may not necessarily be those pursued by the
Norwegian tax system. This issue will, however, be assessed in the course of the formal investigation proce-
dure.

(1) In the Adria Wien-judgment, the European Court of Justice held that ‘…any justification for the grant of advantages
to undertakings whose activity consists primarily in the production of goods is not to be found in the nature or
general scheme of the taxation system…’., paragraph 49. Furthermore, in the Maribel-case, the Court held that ‘that
the limitation of the increased reductions to certain sectors rendered those reduction measures selective, so that they
fulfilled the condition of specificity.’, paragraphs 28 to 31.

(2) See above, where reference is made to the requirements of cost-internalisation, as stipulated in point 19 of the Envir-

onmental Guidelines.

(3) Commission's decision of 3 April 2002 regarding the dual-use exemption from the climate change levy in the United

Kingdom (State aid No C 18/2001 and C 19/2001)

(4) COM (1997) 30 final, OJ 1997 C 139/14.

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Reduced rate for paper and pulp

Finally, as regards the reduced rate for the paper and pulp industry, the Authority notes that this reduction
is sector-specific. The Norwegian Government has not submitted arguments which would have justified
such a derogation by the nature or general scheme of the CO2 tax system.

Conclusions

The derogations resulting from paragraphs 3.6.3 and 3.6.4 of Chapter 3 of the Regulation on Excise
Duties, as well as the reduced rate for the paper and pulp industry, confer a financial benefit to undertak-
ings covered by the exemptions. Thus, firms using the mineral products in the way described above are
relieved of charges that would normally be borne from their budgets and gives the recipient firms an
advantage over other firms. This advantage is granted through State resources as the State suffers a loss of
State revenues. According to the information submitted by the Norwegian Government, tax expenditure
due to the exemptions was estimated to amount to NOK 2 270 million. The recipient firms exercise an
economic activity on markets on which there is or could be trade between the Contracting Parties or on
which firms from other EEA countries might wish to establish themselves. The exemptions therefore distort
or threaten to distort competition and could affect trade between the Contracting Parties.

Consequently, and based on the information submitted by the Norwegian Government, the Authority has
doubts whether the exemptions from and the reduced rates of the CO2 tax do not constitute aid, as the
Norwegian Government claimed, within the meaning of Article 61(1) of the EEA Agreement.

SO2 tax

The Norwegian Government argued that, as far as the tax on oil refineries represented a ‘new’ tax, it was
selective as it only applied to oil refineries. In order to represent a ‘new’ tax the emission tax had to have a
source, other than mineral oil and coal and coke, and thus a source not previously taxed (e.g. raw oil). As
far as this was the case, the Norwegian Government was of the opinion that the abolition in 2002 of the
selective tax measure could not be regarded as selective in the sense that it represents ‘aid’ within Article
61(1) of the EEA Agreement.

The Norwegian Government expressed the view that the abolition of the tax on coal and coke could fall
outside the scope of Article 61(1) of the EEA Agreement.

The Norwegian Government argued that for a measure to be selective it had to be an exemption/reduction
from a general tax scheme directed at a particular sector of the economy or a particular region. A tax
system that taxed, e.g. some products or a certain conduct, as opposed to others, was not selective in
nature. Hence, the abolishment of the SO2 tax on the use of coal and coke could not, in the Norwegian
Government's point of view, be considered as aid within the meaning of Article 61(1) of the EEA Agree-
ment.

The Authority has examined whether the decision to exclude coal and coke as well as emissions from oil
refinery plants has the effect of
favouring the production of certain goods or certain undertakings
compared with other undertakings which are in a legal and factual situation that is comparable in the light
of the objective pursued by the measure in question.

At the outset, the Authority notes that the abolishment of the SO2 tax on coal and coke limits the scope of
the SO2 tax without, however, distinguishing between different categories of undertakings or sectors. The
scope of the SO2 tax is determined by excluding a specific product, namely the use of coal and coke. The
abolishment of the SO2 tax on coal and coke benefits, in principle, all undertakings in Norway using coal
and coke. However, there are indications that the abolishment is targeted at specific sectors of the industry.
Based on information at the Authority's disposal, it would seem that the extension of the scope in 1999, as
well as the limitation of the scope in 2002, concerned around 30 enterprises in the following sectors: oil
refineries, cement and leca production, carbide, aluminium and ferro-alloy industry (1). As regards the abol-
ishment of the SO2 tax for oil refineries, the Authority takes the view that this limitation of the scope of
the SO2 tax is sector-specific. In addition, the Authority observes that these industries are subject to the
agreement of intent concluded between the Norwegian Government and PIL. Due to the link between the
abolishment of the tax and the agreement, the abolishment of the SO2 tax can be seen as being targeted at
the industries covered by the agreement.

(1) This information is taken from the Government paper on Green Taxes, St.prp. nr. 54 (1997-98), Chapter 6 point

6.2.5.

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In view of the overall objective to reduce SO2 emissions, it would seem reasonable for any tax system
targeting SO2 emissions to cover the major part of the emissions; on the other hand, a limitation of the
scope of the tax system which would result in only a minor part of those emitting SO2 being subject to the
tax would at first glance not seem to be in line with the objectives as defined by the Norwegian Govern-
ment.

In this respect, the Authority notes however that according to information available to the Authority,
before the extension of the scope of the SO2 tax, only around 20 % of all SO2 emissions were subject to
the tax (1). After the extension of the scope of the tax, around 80 % of SO2 emissions were covered (2).

The abolishment leads to a situation where not all industries causing SO2 emissions actually pay for such
emissions in the form of an SO2 tax. Therefore, taking account of the objectives pursued by the SO2 tax,
the Authority cannot exclude that the abolishment of the SO2 tax leads to a different tax treatment between
industries which are — from the environmental point of view — in a comparable situation.

Furthermore, without more detailed information on this point, the Authority cannot exclude that the abol-
ishment of the tax on the use of coal and coke as fuel may benefit certain undertakings compared to
undertakings in the process industry using mineral oil for fuel purposes. There may, therefore, be a distor-
tion of competition within the various industry sectors depending on the degree they make use of taxed
and non-taxed products (3).

In light of the above considerations and based on the information at its disposal, the Authority concluded
that the abolishment of the SO2 tax for coal and coke and on oil refineries confers a financial benefit to
undertakings in certain sectors and is thus, in its effects, comparable to a tax exemption. The Norwegian
Government has, in practice, waived their right to receive tax payments from firms in these sectors, thus
conferring upon them an economic advantage.

Consequently, that advantage was conferred through the use of State resources. According to information
at the Authority's disposal (4), based on the current rate of SO2 tax of NOK 3,09 per kg, the duty would
have provided annual tax revenues of approximately NOK 40 to 50 million. The figures presented by the
Norwegian Government regarding tax expenditures due to the SO2 tax exemptions indicate that, from
2001 to 2002, the expected losses in tax revenues were estimated to decrease by NOK 60 million.

The recipient firms exercise an economic activity on markets on which there is or could be trade between
the Contracting Parties or on which firms from other EEA countries might wish to establish themselves.
The exemptions therefore distort or threaten to distort competition and could affect trade between the
Contracting Parties.

Consequently and based on the information at the Authority's disposal, the Authority takes the view that
the abolishment of the SO2 tax may be regarded as aid within the meaning of Article 61(1) of the EEA
Agreement.

Qualification as ‘new aid’ as from 1 January 2002

By accepting the appropriate measures proposed by the Authority (see letter from the Norwegian Govern-
ment dated 6 July 2001), the Norwegian Government was legally bound to bringing existing aid schemes
in line with the requirements set out in the Environmental Guidelines before 1 January 2002 (5).

(1) See Government paper on Green Taxes, St.prp. nr. 54 (1997-98), Chapter 6 point 6.2.5.
(2) St. prp. nr. 1 (2001-2002) — FIN, point 3.11.
(3) It would seem that at least insomuch as these products are used as heating fuels, they are substitutable; see Proposal
for a Council Directive restructuring the Community framework for the taxation of energy products: ‘It is clear that
all these products, inasmuch as they are used as heating fuels, are directly or indirectly substitutable and therefore
should all come with the same taxation framework.’

(4) PIL News dated 18 December 2001,
‘Norwegian Process Industry takes responsibility for reduced SO2-emissions.’
(5) It results from the case law of the European Court of Justice that appropriate measures, accepted by the States
concerned, have a binding effect; see Judgment of the European Court of Justice of 24 March 1993, Case C-313/90,
Comité International de la Rayonne et des Fibres Synthétiques and others v. Commission [1993] ECR p. I-1125.

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The Authority would like to point out that, had the Norwegian Government not signified its agreement to
the appropriate measures, the Authority would have been obliged to open the formal investigation proce-
dure against all existing aid schemes in place in Norway should the Authority have had doubts as regards
their compliance with the new Environmental Guidelines (1). To the extent certain measures had been
found to be incompatible with the requirements laid down in the new Environmental Guidelines, the
Authority would have asked the Norwegian Government to adopt the necessary measures to ensure
compliance or otherwise abolish the aid measures in question. The fact that the Norwegian Government
accepted the appropriate measures but did not adopt the necessary measures to comply with the obliga-
tions resulting therefrom cannot lead to a situation where the Norwegian Government escapes the legal
consequences of its acceptance.

With the acceptance of the appropriate measures, the Norwegian Government assumed obligations which
imply that any aid scheme which is not in accordance with the requirements set out in the new Environ-
mental Guidelines would have to be abolished as from 1 January 2002. With the acceptance, the Norwe-
gian Government assumed obligations it cannot unilaterally deviate from.

The Authority takes note of the request from the part of the Norwegian Government to allow it additional
time for complying with the requirements laid down in the Environmental Guidelines in light of the find-
ings of the working group which was asked to deliver a preliminary report by 1 July 2002.

The Authority observes that it has not been formally informed about the conclusions of the preliminary
report, nor has the Norwegian Government indicated which measures it might intend to take in accordance
with the findings of that report. The Authority notes that more than 14 months after the entry into force
of the new Environmental Guidelines, there are still no concrete proposals from the Norwegian Govern-
ment of how existing aid schemes will be amended so as to be in accordance with the requirements set out
in the new Environmental Guidelines. Without such concrete proposals or commitments, it is impossible
for the Authority to ascertain that existing aid schemes would in fact be in line with the new Environ-
mental Guidelines, albeit at a later date than initially foreseen.

The Norwegian Government has not submitted information which would have demonstrated that the
adoption of appropriate measures necessary to comply with the requirements laid down in the new Envir-
onmental Guidelines would take more time than foreseen under the appropriate measures. In addition, the
Norwegian Government has not claimed that it would not be possible to adopt measures which would
allow the elimination of possible incompatible aid with retroactive effect, i.e. as from 1 January 2002.

In light of the foregoing considerations, the Authority takes the view that the Norwegian Government has
not submitted arguments justifying an extension of the time limit for compliance.

The Authority, therefore, takes the initial view that any aid scheme applicable after 1 January 2002, and
which is found to be incompatible with the requirements laid down in the new Environmental Guidelines,
is to be regarded as ‘new aid’ (2).

The Authority reminds the Norwegian Government that, in accordance with point 6.2.3 of Chapter 6 of
the Authority's State Aid Guidelines, unlawful aid may be recovered from the recipients should the
Authority find the compensation scheme to be incompatible with the EEA Agreement.

Compatibility of aid measures

Assessment of the aid measure under Article 61 (3)(c) of the EEA Agreement in combination with
Chapter 15 of the Authority's State Aid Guidelines on Aid for Environmental Protection

‘[w]hen adopting taxes that are to be levied on
Pursuant to point 42 of the Environmental Guidelines,
certain activities for reasons of environmental protection, EFTA States may deem it necessary to make
provisions for temporary exemptions for certain firms notably because of the absence of harmonisation at
European level or because of the temporary risks of a loss of international competitiveness.’

(1) See point 7.4.3(2) of Chapter 7 in combination with Chapter 5 of the Authority's State Aid Guidelines, in particular

point 5.2(1) thereof.

(2) See Judgment of the European Court of Justice of 24 March 1993, Case C-313/90, CIRFS v. Commission [1993] ECR
I-1125, paragraph 35; see also EC Commission's decision to open the formal investigation procedure in the State aid
case No C 37/2000 (ex NN 60/2000, ex E 19/94, ex E 13/91 and N 204/86) regarding the financial and tax aid
scheme for the free zone of Madeira (Portugal), published in OJ 2000 C 301/4, and EC Commission's decision to
adopt appropriate measures in the State aid case No E 10/2000 regarding the ‘Gewährträgerhaftung und Anstaltslast’
in Germany, letter to Germany dated 27 March 2002.

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According to the guidelines, such exemptions constitute operating aid but that ‘…the adverse effects of
such aid can be offset by the positive effect of adopting taxes. Accordingly, if such exemptions are neces-
sary to ensure the adoption or continued application of taxes applicable to all products, the Authority takes
the view that they are acceptable, subject to certain conditions and for a limited period of time. This period
may last for 10 years if the conditions are met…’

Pursuant to point 43 of the Environmental Guidelines, ‘[i]f the tax does not correspond to a tax which is
to be levied within the European Community as the result of a Community decision, the firms affected
may have some difficulty in adapting rapidly to the new tax burden. In such circumstances there may be
justification for a temporary exemption enabling certain firms to adapt to the new situation.’

In the following, the guidelines lay down the specific requirements which must be fulfilled in order to
benefit from the 10-year exemption (see point 46 of the Environmental Guidelines). The requirements
depend also on whether or not the tax in question concerns a tax which corresponds to a harmonised tax
at Community level.

The Authority points out that exemptions may, in principle, only be approved under the Environmental
Guidelines with respect to ‘new environmental taxes’. This means, on the one hand, that the tax in question
must be an ‘environmental tax’ as defined in point 7 of the guidelines. This implies that the EFTA State
concerned has to demonstrate the estimated environmental effect of the levy. In addition, the exemptions
in question must be granted with respect to a newly introduced tax. For ‘existing taxes’ the EFTA State
concerned would have to demonstrate that the conditions enumerated under point 46.2 or point 47 of the
Environmental Guidelines are fulfilled.

In general, and in cases where no corresponding harmonised Community tax exists, a 10-year exemption
may be justified where exemptions from the tax are conditional upon the conclusion of agreements in
which beneficiary firms give undertakings to achieve environmental protection objectives or where the
exemptions are subject to conditions that have the same effects (see point 46.1(a)). Point 46.1(a) lays down
further criteria which have to be met in order for the agreement/commitment to be regarded as justified. It
is for the Authority to assess the substance of the agreements. EFTA States must ensure strict monitoring
of the commitments entered into by the firms or associations of firms. The agreements concluded between
an EFTA State and the firms concerned must stipulate the penalty arrangements applicable if the commit-
ments are not met.

In the absence of such agreements and undertakings, derogations from the tax in question may be granted
if the eligible firms pay a significant proportion of the national tax (see point 46.1(b) second alternative).
On the other hand, where the reduction concerns a tax corresponding to a harmonised Community tax,
the guidelines require that the amount effectively paid by the eligible undertakings must remain higher
than the Community minimum in order to provide an incentive to improve environmental protection (see
point 46.1(b) first alternative).

Finally, the EFTA State concerned would have to show that the tax measure in question makes a significant
contribution to protecting the environment and that the exemptions do not, by their very nature, under-
mine the general objectives pursued (see point 45 of the Guidelines).

Electricity tax

At the outset, the Authority takes note of the fact that, according to the Norwegian Government, a
working group has been set up in order to examine the consequences of the new Environmental Guidelines
for the electricity tax in Norway. This working group was asked to deliver a preliminary report by 1 July
2002. Any measures addressed by the working group would be assessed by the Norwegian Government in
the context of the State Budget for 2003. No further information or justification was provided by the
Norwegian Government as regards exemptions from the electricity tax and their compatibility under the
Environmental Guidelines.

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The Authority notes that there is currently no harmonised electricity tax at Community level. However,
several EC Member States have introduced taxes on the consumption of electricity. These taxes show big
differences in the applicable rates and the tax structure, including exemptions and refund mechanisms.
These differences make it difficult to compare the electricity tax systems in other EC Member States to that
in place in Norway. The Authority takes note of the information submitted by the Norwegian Government
regarding the estimated increase in costs resulting from a withdrawal of the tax exemptions. These figures
may indicate that, at least for some industries, there is a necessity to offset costs due to the electricity tax.
Against this background, exemptions under the Norwegian electricity tax system for certain industries
might be regarded as justified in order to offset losses of competitiveness.

However, in order to strike a balance between environmental concerns and concerns regarding the mainte-
nance of competitive conditions for certain industries, the exemptions in question have to satisfy the
requirements laid down in the new Environmental Guidelines.

Based on the scarce information provided by the Norwegian Government as regards the justification of the
sectoral derogations from the electricity tax under the new Environmental Guidelines the Authority makes
the following observations:

First of all, the Authority notes that the electricity tax was introduced in 1971 and is therefore to be
regarded as an ‘existing tax’. Based on the information submitted by the Norwegian Government, it would
seem that various tax exemptions were adopted after the tax was introduced. The Norwegian Government
has not provided an explanation as to how the exemption possibility in point 46.1 of the Environmental
Guidelines could apply to exemptions from existing tax measures. In particular, the Authority notes that in
1993, 1994 and 1997, when additional exemptions were introduced, the tax rate had not been increased
significantly. As regards exemptions granted in, and possibly before, 1993 the Authority has no informa-
tion.

In addition, the Norwegian Government has submitted only general statements regarding the objectives of
the electricity tax. It has, however, not provided information required in accordance with point 7 of the
Environmental Guidelines, showing that the electricity tax has positive environmental effects.

Contrary to the conditions stipulated in point 46.1 of the Environmental Guidelines, the exemption is
neither conditional on the conclusion of environmental agreements, nor do firms eligible for an exemption
pay a significant proportion of the national tax (since they are totally exempted). In this respect, the
Authority points out that the figures presented by the Norwegian Government regarding the estimated
increase in costs due to the abolishment of the existing exemptions from the electricity tax cannot in them-
selves justify the exemptions. These figures need to be assessed in more detail in the context of determining
what could be the regarded as a ‘significant proportion’ of the national tax, which would have to be paid
by the companies concerned in order to benefit from the derogation possibility in point 46.1(b) of the
Environmental Guidelines.

Contrary to the requirements laid down in point 45 of the Environmental Guidelines, the Norwegian
Government has not shown that the exemptions do not undermine the general objectives of the electricity
tax. With approximately 70 % of consumption of electricity by the industry in Norway being exempted,
the Authority is not convinced that the objective of the tax, i.e. the reduction of electricity consumption,
has been achieved despite the broad exemption possibilities.

Finally, the Norwegian Government has neither shown that the derogations are temporary, nor have they
given any commitment as regards the limitation of the aid measures in time.

As regards the regional derogations from the electricity tax, the Norwegian Government pointed out the
special need for use of electricity in the eligible areas. It pointed out that harsh weather conditions and the
long distances in this particular area would make the external conditions hard for business activities, and
the exemption might, therefore, be justified as regional development aid. Furthermore, the exemption
covered every industry, and no single company is discriminated by this exemption.

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Even though the Authority explicitly requested the Norwegian authorities to provide a proper justification
of the measures in question, the Authority notes that no such justification has been provided (the Norwe-
gian Government merely stated that it is for the working group to consider alternative tax structures that
are expected to be in line with the new Environmental Guidelines). In the absence of a justification, the
Authority has doubts that the regional derogations could be regarded as compatible with the EEA State aid
rules.

In light of the foregoing considerations, the Authority has doubts that the exemptions from the electricity
tax are compatible with the functioning of the EEA Agreement.

CO2 tax

The Authority notes that there is currently no harmonised CO2 tax at Community level. To the Authority's
knowledge, several EC Member States have introduced CO2 taxes (in particular in Denmark, Sweden,
Finland and the Netherlands) (1). The tax rates and the structure, including tax base, applicable exemptions
and refund schemes show, however, big differences. These differences make it difficult to compare the CO2
tax systems in other EC Member States to that in place in Norway. The Authority takes note of the infor-
mation submitted by the Norwegian Government regarding costs of the CO2 tax for certain industries.
These figures might indicate that, at least for certain sectors of industry, there is a necessity to offset costs
due to the CO2 tax. Against this background, exemptions under the Norwegian CO2 tax system for certain
industries might be regarded as justified in order to offset losses of competitiveness.

However, in order to strike a balance between environmental concerns and concerns regarding the mainte-
nance of competitive conditions for certain industries, the exemptions in question have to satisfy the
requirements laid down in the new Environmental Guidelines.

Contrary to the conditions stipulated in point 46.1 of the Environmental Guidelines, the exemptions from
the CO2 tax are neither conditional on the conclusion of environmental agreements, nor do firms eligible
for an exemption/refund seem to pay a significant proportion of the national tax (since they are totally
exempted; where the tax is refunded, the Authority would need information about the level of compensa-
tion in order to assess whether the companies concerned still pay a significant proportion of the tax).

As regards the environmental effects of the CO2 tax, the Authority regrets that no information was
submitted in accordance with point 7 of the Environmental Guidelines, which would have shown the
effects of the CO2 tax on reduction of CO2 emissions.

Contrary to the requirements laid down in point 45 of the Environmental Guidelines, the Norwegian
Government has not shown that the exemptions do not undermine the general objectives of the CO2 tax.
In this respect, the Authority takes note of the information submitted by the Norwegian Government
regarding CO2 emissions caused by certain industries. From this information it would appear that the CO2
emissions caused by industries exempted from the CO2 tax account for approximately 66 % of overall CO2
emissions. Against this background, the Authority has doubts whether the requirement in point 45 of the
Environmental Guidelines is fulfilled.

Contrary to what is required under point 43 of the Environmental Guidelines, the Norwegian Government
has neither shown that the derogations are temporary nor have they given any commitment as regards the
limitation of the aid measures in time.

As regards the application of a reduced rate for the paper and pulp industry, the Norwegian Government
has claimed that the reduced rate to be paid by this industry would exceed the corresponding EC tax,
which is EUR 18 per 1 000 litres (NOK 0,14 per litre). Therefore, the Norwegian Government regarded
the reduced tax to be in line with section 46.1(b) alternative 1.

(1) See overview of environmental taxes in the EU, in Report to DG Environment, Update of Database of Environmental
Taxes and Charges, Stefan Speck and Paul Ekins, July 2000; see also EC database on environmental taxes:http://euro-
pa.eu.int/comm/environment/enveco/env_database/database.htm.

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As the Authority has stated above, there is currently no harmonised CO2 tax at Community level. There-
fore, it would not seem that point 46.1(b) first alternative of the Environmental Guidelines is applicable. In
addition, the Authority notes that no further information was submitted which would have shown that this
rate provided firms in the paper and pulp industry with an incentive to improve environmental protection.

As regards the possibility for a temporary exemption under point 46.1(b) second alternative of the Envir-
onmental Guidelines, the Authority notes that the reduced tax rate amounts to 50 % of the normal CO2
tax rate. The Authority does not exclude that this percentage could be regarded as a ‘significant proportion’
of the national tax. However, and as already pointed out in the previous paragraph, without information
on the effects of this reduced rate on the behaviour of the industry concerned and in particular whether
this rate still serves as an incentive to improve environmental protection, the Authority cannot conclude
that the requirements in the guidelines are fulfilled.

Finally, the Authority observes that the CO2 tax on mineral oil introduced in 1991 constitutes an ‘existing
tax’. The Authority notes that, according to the information submitted by the Norwegian Government, the
reduced rate for the paper and pulp industry was only later introduced, i.e. in 1993. Against this back-
ground, the Authority has doubts whether the conditions laid down in point 46.2 of the Environmental
Guidelines are satisfied, since the derogation from the generally applicable rate would seem not to have
been decided on when the tax was adopted. In addition, the Authority notes that the Norwegian Govern-
ment has not submitted information enabling the Authority to assess whether an exemption under point
46.1. of the Environmental Guidelines was justified under these circumstances.

In light of the above considerations, and should the further investigation confirm that the measures in
question constitute aid within the meaning of Article 61(1) of the EEA Agreement, the Authority has
doubts that the requirements laid down in the Environmental Guidelines are fulfilled with respect to the
derogations from the CO2 tax.

SO2 tax

The Authority notes at the outset that there is currently no harmonised SO2 tax at Community level. To
the Authority's knowledge, several EC Member States have introduced SO2 taxes (in particular Finland,
Sweden and Denmark) (1). The tax rates and the structure, including exemptions and refund schemes show,
however, big differences. These differences make it difficult to compare the SO2 tax systems in other EC
Member States to that in place in Norway. The Authority takes note of the information submitted by the
Norwegian Government regarding costs of the SO2 tax for certain industries. These figures might indicate
that, at least for certain sectors of industry, there is a necessity to offset costs due to the SO2 tax. Against
this background, exemptions under the Norwegian SO2 tax system for certain industries might be regarded
as justified in order to offset losses of competitiveness.

However, in order to strike a balance between environmental concerns and concerns regarding the mainte-
nance of competitive conditions for certain industries, the exemptions in question have to satisfy the
requirements laid down in the new Environmental Guidelines.

According to the Norwegian Government (see letter dated 31 January 2002), the exemptions from taxes,
such as no tax on use of coal and coke and on the refineries, were in line with the Environmental Guide-
lines.

The Norwegian Government claimed that the abolishment of the tax was conditional on the conclusion of
the agreement and that the abolishment of the tax could be seen as temporary. In this respect, it referred
to a declaration in the State Budget for 2002 (St.prp. nr. 1 (2001-2002)): ‘As part of the Agreement with
PIL, the reduced tax on coal and coke and on oil refineries shall be abolished for the period up to 2010.’
The Norwegian Government further informed the Authority that it had also been indicated in the context
of the State Budget 2002 that it was the Norwegian Government's intention to phase out the existing tax
exemption within 2010.

(1) See overview of environmental taxes in the EU, in Report to DG Environment, Update of Database of Environmental

Taxes and Charges, Stefan Speck and Paul Ekins, July 2000; see also EC database on environmental taxes:
http://europa.eu.int/comm/environment/enveco/env_database/database.htm.

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The Authority points out that, even though the Norwegian Government stated that its intention was to
phase out the existing ‘tax exemption’ within 2010, the Authority notes that no formal commitment,
which would have limited the duration of the tax exemption to a maximum of ten years in a legally
binding way, has been given by the Norwegian Government. Therefore, the Authority does not consider
the aid to be of only temporary nature, as required under point 43 of the Environmental Guidelines.

Furthermore, the Authority notes that the SO2 tax is not a ‘new tax’ within the meaning of point 46.1 of
the Environmental Guidelines. According to point 46.2 of the Environmental Guidelines, the provisions in
point 46.1 may be applied to existing taxes if certain conditions are fulfilled. In this respect, the Authority
notes that the Norwegian Government has not provided a justification for why the exemption possibility
in point 46.1 of the Environmental Guidelines is applicable in the present case.

More importantly, the Authority has doubts whether the conclusion of an agreement of intent between the
Federation of Norwegian Process Industries (PIL) and the Ministry of Environment, as well as the adoption
of possible future permission limits/permits by the Norwegian Pollution Control Authority fulfil the
requirements set out under point 46.1 of the Environmental Guidelines.

As the Authority has already pointed out in its letter dated 28 February 2002, the agreement of intent is
not legally binding upon the parties. Furthermore, the abolishment of the SO2 tax would not seem to be
conditional upon the implementation of the measures envisaged under the agreement of intent. The state-
ment in the State Budget for 2002 can hardly be seen as sufficient. In this respect, the Authority notes, in
particular, that there are no sanctions in case the commitments given by the undertakings benefiting from
the tax exemption are not fulfilled. Finally, it is not clear to the Authority whether the obligation to reduce
SO2 emissions will result from the agreement or emission permits to be issued by the Norwegian Pollution
Control Authority.

In order to benefit from a ten-year exemption, the Environmental Guidelines require that commitments
given under agreements or other provisions having the same effects will result in reductions in emissions
on the part of the firms benefiting from the exemption which go beyond normal business. The environ-
mental effects of the agreements, or other provisions having the same effect, must be at least as good as
the environmental effect of the taxes they replace.

The Norwegian Government informed the Authority, by letter dated 15 May 2002, that SO2 emissions
from the process industry were already subject to legally binding regulations through emission permits in
accordance with the provisions of the Pollution Control Act. These regulations had already led to SO2 emis-
sion reductions at costs higher than NOK 3/kg SO2. From 1990 to 2000, emissions from industrial
processes were reduced by 13 500 tonnes, to 17 100 tonnes in 2000. Only 800 tonnes of this reduction
took place from 1998 to 2000, when the SO2 tax was in force (1).

The Authority observes, however, that, at present, no concrete commitments as regards such reductions
have been given by the sector benefiting from the exemption from the SO2 tax, nor has the Authority
more detailed information on the content of the future emission permits.

The information submitted by the Norwegian Government with respect to reductions of SO2 emission due
to the previous tax regime might indicate that the efforts to be undertaken by the industry concerned until
2010 go beyond what has been achieved so far in terms of SO2 emissions with the tax in place. However,
given the lack of more detailed and verifiable information, the Authority is not able to ascertain that the
company's efforts under the agreement of intent or in the context of future binding emission limits set by
the Norwegian Pollution Control Authority are in proportion to the tax exemption.

(1) The Norwegian Government informed the Authority that emission data for 2001 was not yet available.

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In addition, the Authority observes that it is not clear from the information that has been submitted by the
Norwegian Government whether emission permits issued in the past as well as possible future emission
limits exceed binding Community standards within the meaning of the Environmental Guidelines. Point 7
of the Environmental Guidelines defines ‘Community standard’ as being the standard mandatory within the
European Community setting the levels to be attained in environmental terms and the obligation to use the
best available techniques (BAT) which do not entail excessive costs (1). In this respect, the Authority notes
that no information was submitted which would have allowed the Authority to examine whether and to
what extent such possible future limits for SO2 emissions would exceed harmonised standards, such as the
limits laid down in the EEC Directive on air quality standards for sulphur dioxide (2) and whether such
future limits would exceed the requirements following the Directive on air pollution from industrial
plants (3) and the ‘IPPC’ Directive (4).

In light of the above considerations, and should the further investigation confirm that the measures in
question constitute aid within the meaning of Article 61(1) of the EEA Agreement, the Authority has
doubts that the requirements laid down in the Environmental Guidelines are fulfilled with respect to the
partial abolition of the SO2 tax.

Final remarks and conclusions

Based on the information submitted by the Norwegian Government, the Authority cannot exclude that the
exemptions from the electricity tax, derogations from the CO2 tax as well as the abolition of the SO2 tax
constitute aid within the meaning of Article 61(1) of the EEA Agreement. Furthermore, the Authority has
doubts that these measures can be regarded as complying with Article 61(3)(c) of the EEA Agreement, in
combination with the requirements laid down in the new Environmental Guidelines. Consequently, the
Authority has doubts that the above measures are compatible with the functioning of the EEA Agreement.

Consequently, and in accordance with point 5.2 of Chapter 5 of the Authority's State Aid Guidelines, the
Authority is obliged to open the procedure provided for in Article 1(2) of Protocol 3 of the Surveillance
and Court Agreement. The decision to open proceedings is without prejudice to the final decision of the
Authority, which may conclude that the measures in question are compatible with the functioning of the
EEA Agreement,

HAS ADOPTED THIS DECISION:

1. The Authority has decided to open the formal investigation procedure provided for in Article 1(2) of

Protocol 3 to the Surveillance and Court Agreement against:

— the sectoral and regional exemptions from the tax on electricity consumption;

— the exemptions from the CO2 tax for coal and coke used as raw materials or as reducing agents in
industrial processes as well as for coal and coke used for energy purposes in the production of
cement and leca and the reduced CO2 tax rate for the paper and pulp industry; and

— the abolition of the SO2 tax for coal and coke as well as for the oil refinery industry.

2. The Norwegian Government is invited, pursuant to point 5.3.1(1) of Chapter 5 of the Authority's State
Aid Guidelines, to submit its comments on the opening of the formal investigation procedure within
two months from the notification of this Decision.

(1) In footnote 5 to the Environmental Guidelines, it is clarified that such standards become EEA standards when they
are incorporated into the EEA Agreement. In footnote 6 to the Environmental Guidelines, reference is made to the
relevant EC Directives as incorporated into the EEA Agreement.

(2) Council Directive 80/779/EEC, incorporated into the EEA Agreement, point 14 of Annex XX to the EEA Agreement.
(3) Council Directive 84/360/EEC of 28 June 1984 on the combating of air pollution from industrial plants, incorpo-

rated into the EEA Agreement in point 16 of Annex XX to the EEA Agreement.

(4) Council Directive 96/61/EC of 24 September 1996 concerning integrated pollution prevention and control, incorpo-

rated into the EEA Agreement in point 2g of Annex XX to the EEA Agreement.

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3. The Norwegian Government is requested to submit all information enabling the Authority to examine
the compatibility of the tax measures in question with the EEA Agreement within two months from the
notification of this Decision.

Done at Brussels, 26 July 2002.

For the EFTA Surveillance Authority

Einar M. BULL

The President