Decyzja nr 039/24/COL z dnia 27 marca 2024 r. o wszczęciu formalnego postępowania wyjaśniającego w sprawie zwolnień z podatku akcyzowego obejmującego spalanie odpadów oraz z podatku od emisji CO2 obejmującego gaz płynny (LPG) i gaz ziemny w przypadku przedsiębiorstw objętych systemem ETSZaproszenie do zgłaszania uwag dotyczących pomocy państwa zgodnie z częścią II art. 4 ust. 4 i częścią I art. 1 ust. 2 protokołu 3 do Porozumienia między państwami EFTA w sprawie ustanowienia Urzędu Nadzoru i Trybunału Sprawiedliwości w odniesieniu do wyżej wymienionych środków
(C/2024/3127)
(Dz.U.UE C z dnia 8 maja 2024 r.)
Zainteresowane strony mogą zgłaszać uwagi na temat przedmiotowego środka pomocy w terminie jednego miesiąca od daty publikacji na adres Urzędu Nadzoru EFTA:
EFTA Surveillance Authority
Registry
Avenue des Arts 19H
1000 Brussels
Belgia
registry@eftasurv.int
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Streszczenie
Procedura
Pismem z dnia 29 lutego 2024 r. władze norweskie zgłosiły dwa odrębne środki opisane poniżej.
Opis przedmiotowych środków
Środek 1: W 2022 r. Norwegia wprowadziła podatek akcyzowy od emisji CO2 pochodzących ze spalania odpadów. Celem podatku akcyzowego jest internalizacja kosztów emisji CO2 związanych ze spalaniem odpadów.
Norweska ustawa o kwotach klimatycznych wdraża obowiązki Norwegii zgodnie z dyrektywą w sprawie europejskiego systemu handlu uprawnieniami do emisji (dyrektywa 2003/87/WE). W ramach zakresu stosowania wspomnianej dyrektywy ustawa o kwotach klimatycznych nakłada na przedsiębiorstwa obowiązek posiadania i umarzania uprawnień do emisji z tytułu własnych emisji gazów cieplarnianych, co służy internalizacji kosztów emisji takich gazów.
Zgłoszony system zwalnia przedsiębiorstwa już objęte systemem EU ETS z podatku akcyzowego od spalania odpadów.
Środek 2: Rząd Norwegii zaproponował wprowadzenie podatku od emisji CO2 obejmującego gaz ziemny i LPG, które są wykorzystywane w redukcji chemicznej lub w elektrolizie oraz procesach metalurgicznych i mineralogicznych ("przemysł przetwórczy"). Za pośrednictwem zgłoszonego programu władze norweskie planują zwolnić z podatku od emisji CO2 przedsiębiorstwa w przemyśle przetwórczym, które objęte są systemem EU ETS.
Wstępna ocena istnienia pomocy zgodnie z art. 61 ust. 1 Porozumienia EOG
Władze norweskie twierdzą, że środki nie kwalifikują się jako pomoc państwa, ponieważ nie są selektywne w rozumieniu art. 61 ust. 1 Porozumienia EOG.
Środki uznaje się za selektywne, jeżeli sprzyjają niektórym przedsiębiorstwom lub produkcji niektórych towarów w porównaniu z innymi przedsiębiorstwami znajdującymi się w porównywalnej sytuacji prawnej i faktycznej, jeśli chodzi o cel realizowany przez dany środek.
Ocena selektywności środków podatkowych przebiega zazwyczaj w drodze trzyetapowej analizy. Po pierwsze, określa się system odniesienia. Po drugie, dokonuje się oceny, czy dany środek stanowi odstępstwo od systemu. Odstępstwo istnieje, jeżeli środek wprowadza zróżnicowanie przedsiębiorstw, które znajdują się - biorąc pod uwagę cele realizowane przez system - w porównywalnej sytuacji prawnej lub faktycznej. Po trzecie, należy ocenić, czy dany środek jest uzasadniony charakterem lub ogólną strukturą ram odniesienia.
Środek 1: Na tym etapie jako system odniesienia Urząd Nadzoru EFTA (dalej "Urząd") określił podatek akcyzowy obejmujący działania związane ze spalaniem odpadów, w wyniku czego do atmosfery uwalniany jest kopalny CO2. W odniesieniu do takiego podatku akcyzowego Urząd wstępnie uznał, że objęcie przedsiębiorstwa systemem ETS nie wydaje się samo w sobie wystarczające do stwierdzenia, że znajduje się ono w innej sytuacji prawnej i faktycznej. Ponieważ cel i logika systemu odniesienia polegają na wprowadzeniu specyficznego podatku akcyzowego od wszystkich emisji CO2 ze spalania odpadów, środek 1 nie wydaje się być zgodny z charakterem lub ogólną strukturą systemu odniesienia.
Środek 2: W decyzji o wszczęciu postępowania jako system odniesienia Urząd określił podatek od emisji CO2 obejmujący produkty mineralne powodujące emisje CO2. Urząd wstępnie uznał, że istotnym celem podatku jest objęcie emisji CO2 z produktów mineralnych podatkiem od jednostki emisji. Podobnie jak w przypadku środka 1 Urząd wstępnie stwierdził, że przedsiębiorstwa nie znajdują się w innej sytuacji prawnej lub faktycznej tylko dlatego, że ich działalność jest (lub nie jest) objęta systemem ETS. Wydaje się, że środek nie jest zgodny z charakterem lub ogólną strukturą systemu odniesienia.
Na obecnym etapie Urząd uważa, że spełnione są kryteria określone w art. 61 ust. 1 Porozumienia EOG w odniesieniu do obu środków: środki te przyznają beneficjentom selektywne korzyści, które zwalniają ich z kosztów, które by normalnie ponosili. Zwolnienia podatkowe są ponadto przyznawane przez państwo przy użyciu zasobów państwowych. Może to zakłócać konkurencję i negatywnie wpływać na handel między umawiającymi się stronami.
Ocena zgodności
Władze Norwegii nie przedstawiły informacji dotyczących zgodności środków z jednym z odstępstw od zakazu pomocy państwa określonych w art. 61 ust. 1 Porozumienia EOG. W związku z tym Urząd ma wątpliwości co do zgodności środków z funkcjonowaniem Porozumienia EOG.
Niemniej jednak Urząd określił kilka możliwych powodów (częściowej) zgodności i zwrócił się do władz norweskich o przedstawienie uwag na ten temat. Podstawy prawne ewentualnej zgodności z Porozumieniem EOG obejmują art. 61 ust. 3 lit. c) Porozumienia EOG w związku z wytycznymi Urzędu dotyczącymi pomocy państwa na ochronę klimatu i środowiska oraz cele związane z energią, bezpośrednio art. 61 ust. 3 lit. c) Porozumienia EOG oraz art. 44a ogólnego rozporządzenia w sprawie wyłączeń grupowych.
Brussels, 27 March 2024
Case No: 91767
Document No: 1361782
Decision No: 039/24/COL
Ministry of Trade, Industry and Fisheries
PO Box 8090 Dep
0032 Oslo
Norway
Decision opening a formal investigation into the exemptions from excise duty on waste incineration and CO2 tax on LPG and natural gas for undertakings covered by the ETS
1 Summary
(1) The EFTA Surveillance Authority ('ESA') wishes to inform the Norwegian authorities that, after a preliminary examination of i) the exemption from excise duty on waste incineration for undertakings subject to the EU Emissions Trading System ('measure 1') and ii) the exemption from CO2 tax for liquefied petroleum gas ('LPG') and natural gas for the processing industry for undertakings subject to the EU Emissions Trading System ('measure 2'), ESA has doubts as to whether the measures constitute State aid and, if so, whether the aid is compatible with the functioning of the EEA Agreement. On this basis, ESA has decided to open a formal investigation procedure pursuant to Articles 4(4) in Part II and 1(2) in Part I of Protocol 3 to the Surveillance and Court Agreement ('Protocol 3').
2 Procedure
(2) On 29 February 2024, the Norwegian authorities notified the measures, pursuant to Article 1(3) of Part I of Protocol 3 1 .
3 Description of the measures
3.1 Measure 1
(3) In its budget proposal for 2022, the Norwegian Government proposed to introduce an excise duty on waste incineration to reduce emissions of CO2 by internalising the costs of the CO2 emissions associated with this activity 2 . The excise duty on waste incineration was introduced on 1 January 2022.
(4) The Norwegian Climate Quota Act ('the Climate Quota Act') 3 , has been introduced to implement Norway's obligations pursuant to the EU Emission Trading System Directive ('ETS Directive') 4 . Within its scope of application, the Climate Quota Act imposes an obligation on undertakings to surrender emission allowances as specified in the Climate Quota Act.
(5) Emissions covered by the Climate Quota Act do not currently benefit from a total exemption from the excise duty on waste incineration 5 . However, to avoid that undertakings are both subject to the excise duty on waste incineration, and the obligation to surrender emissions allowances pursuant to the Climate Quota Act, the Norwegian authorities plan to introduce measure 1. If approved by ESA, measure 1 would completely exempt emissions that are covered by the Climate Quota Act from the excise duty on waste incineration.
(6) In the view of the Norwegian authorities, measure 1 does not qualify as State aid within the meaning of Article 61(1) of the EEA Agreement, as it is a non-selective measure.
3.2 Measure 2
(7) In its budget proposal of 12 October 2021, the Norwegian Government proposed to introduce a CO2 tax on natural gas and LPG used in chemical reduction or electrolysis, metallurgical and mineralogical processes ('the CO2 tax for the processing industry').
(8) On the basis of a parallel line of reasoning as for measure 1, the Norwegian authorities plan to exempt activities covered by the Climate Quota Act from the CO2 tax for the processing industry 6 . The Norwegian authorities also consider that measure 2 will not amount to State aid as it will not confer a selective advantage on undertakings.
3.3 Objective
(9) The measures share the same objective of avoiding that activities associated with CO2 emissions are subject to two sets of legislative requirements, which both aim to internalise the costs of the emissions. Measure 1 is designed to ensure that waste incineration is not subject to both an excise duty and the costs of emissions allowances resulting from the Climate Quota Act. Measure 2 will ensure that undertakings in the processing industry are not subject to both the CO2 tax for the processing industry and the costs of emissions allowances resulting from the Climate Quota Act.
3.4 National legal basis
(10) The national legal basis for the measures will be the decisions on excise duties and taxes that are adopted annually by Parliament through the State Budget, and the applicable Norwegian regulations implementing these decisions.
3.5 Administration
(11) The measures will be administered by the Ministry of Finance. The Norwegian tax system is however structured around an obligation of self-assessment. This duty entails that taxpayers are obliged to submit factually correct information to the tax authorities and apply the relevant tax rules to calculate the tax.
3.6 Relevant environmental laws and policies
(12) The European Union is committed to transforming Europe into a highly energy efficient and carbon-neutral economy. To this end, the European Climate Law entered into force on 29 July 2021 7 . It includes a legal objective for the EU to reach climate neutrality by 2050, and a target of at least 55% reductions in the net greenhouse gas emissions compared to 1990 levels by 2030.
(13) As reflected in EEA Joint Committee Decision No 269/2019 8 , Norway agreed in 2019 to new obligations under EEA law to achieve, by 2030, its target of at least a 40% reduction in greenhouse gas emissions compared with 1990-levels following from the Paris Agreement. Following that Joint Committee Decision, Norway is subject to the Effort Sharing Regulation 9 ('the ESR') and the Regulation on Land Use, Land Use Change and Forestry 10 , in addition to the EU Emission Trading System ('the ETS'), which it has been part of since 2008. As part of its 'Fit for 55-package', the EU has revised these acts to reflect the increased target of at least 55% reductions in the net greenhouse gas emissions compared to 1990 levels by 2030 11 . The amendments to the ESR have however not yet been adapted and incorporated into the EEA Agreement, unlike the amendments to the ETS.
3.6.1 The EU Emissions Trading System
(14) The ETS covers emissions from highly emitting industries and activities, such as energy production, the petroleum sector and aviation. The ETS is a so-called cap and trade instrument. It establishes a cap on the total emissions of certain greenhouse gases from the ETS sectors, and a system for issuing and surrendering tradable emissions allowances within this cap. The ETS was set up by Directive 2003/87 and put into effect in 2005. Norway has been part of the system since 2008 12 .
(15) The limit on the total number of allowances, in combination with the obligation to surrender allowances corresponding to the level of emissions, ensures that the ETS contributes to internalising the costs of emissions. Pursuant to the ETS, a number of allowances are however allocated to undertakings free of charge.
(16) Each year, undertakings must surrender allowances corresponding to their emissions covered by the ETS for the previous year. Fines are imposed if this obligation is not complied with. Undertakings that have had lower emissions than the allowances they possess can keep surplus allowances. The cap within the ETS is reduced over time so that total emissions fall.
(17) The ETS was last amended by Directive 2023/959 13 . With effect from 1 January 2024, the amended ETS also covers maritime transport.
(18) In addition to the amendments made to the ETS, an additional emissions trading system was introduced to cover emissions from buildings, road transport and additional sectors which had previously not been covered by the ETS ('ETS 2'). The ETS and the ETS 2 constitute separate emissions trading systems in the sense that allowances are not transferable between them. Activities subject to a duty to surrender emissions allowances pursuant to ETS 2 are excluded from the scope of the notified measure 14 .
(19) In 2023, the price of emission allowances under the ETS averaged approximately 80 Euro per tonnes of CO2 emissions. In February 2024 the price was approximately 60 Euro. The prices of ETS 2 allowances are expected to be lower. This is partially due to a price stabilizing mechanism, which will release additional allowances in the marked if the allowance price surpasses EUR 45. The mechanism will be in place until 2030.
3.6.2 The Effort-Sharing Regulation
(20) According to Article 2(1) of the ESR, the regulation applies to greenhouse gas emissions from energy, industrial processes and product use, agriculture and waste management, excluding greenhouse gas emissions that are covered by the ETS. Emissions subject to the ETS are therefore excluded from the scope of the ESR.
(21) The regulation sets a national target for the reduction of greenhouse gas emissions for each State. It is up to the national authorities in the respective States to implement policy instruments to comply with their national targets.
(22) When incorporating the ESR into the EEA Agreement, the EEA Joint Committee set a national emission reduction target for Norway under the Regulation.
4 Arguments presented by the Norwegian authorities
4.1 Introduction
(23) In the view of the Norwegian authorities, the measures do not constitute State aid, as they are not selective.
4.2 The reference systems
(24) According to the Norwegian authorities, the reference system against which to assess the selectivity of a specialpurpose levy on activities having a negative effect on the environment is normally the levy itself 15 . Following this approach, the relevant reference systems in the present case would be the excise duty on waste incineration for measure 1 or the CO2 tax on mineral products for measure 2.
(25) However, the Norwegian authorities argue that the aim of the excise duty on waste incineration and the CO2 tax on the processing industry is to introduce a price on CO2 emissions where such a price is not levied through alternative instruments. In the view of the Norwegian authorities, the reference system against which to assess measure 1 is therefore the excise duty on waste incineration that falls outside the scope of the ETS but is causing emissions covered by the ESR. As for measure 2, the Norwegian authorities assert that the relevant reference system is the CO2 tax for mineral products causing emissions covered by the ESR.
(26) In support of their assessment, the Norwegian authorities have noted that the excise duty on waste incineration and the CO2 tax for the processing industry will contribute to fulfil Norway's commitments under the ESR. It is up to national authorities to decide on the instruments implemented to cut emissions covered by the ESR. The instrument of choice in Norway is environmental taxes. As environmental taxes are widely considered effective and cost-efficient, it would be illogical if the State aid rules prevented Norway from utilising environmental taxes to reduce its ESR emissions.
(27) Undertakings will pay a price on emissions covered by the ETS as a result of the obligations under this system to surrender sufficient emission allowances to cover annual emissions. Therefore, it is not necessary to make waste incineration and processing industry covered by the ETS subject to additional environmental taxes to attain emissions reductions. To the contrary, exempting such emissions from the taxes applicable in the non-ETS sectors would be consistent with the aim of incentivising emissions reductions in a cost-efficient manner while limiting distortions to competition.
4.3 The measures are not prima facie selective
(28) In the opinion of the Norwegian authorities, undertakings exempted from the excise duty on waste incineration by measure 1 and the CO2 tax for the processing industry by measure 2 are in a different factual and legal situation than those undertakings which are not exempted by virtue of being subject to the ETS. On this basis, the Norwegian authorities assert that the measures do not derogate from the reference systems and are therefore not prima facie selective.
4.4 The derogations are justified by the logic and nature of the reference systems
(29) In the event that ESA should consider that the measures are prima facie selective, the Norwegian authorities argue that they are justified by the logic and nature of the reference systems. In this regard, the Norwegian authorities have underlined that the excise duty on waste incineration, the CO2 tax for the processing industry and the ETS share the same aim of reducing CO2 emissions by imposing a price on such emissions.
(30) Without the exemptions set forth in measures 1 and 2, the concerned emissions would effectively be levied a carbon price twice. As the excise duty on waste incineration and the CO2 tax for the processing industry are intended to provide cost efficient reductions in ESR emissions, preventing double pricing of emissions must be considered a logical consequence of the reference systems.
(31) In addition, the Norwegian authorities have pointed out that Directive 2023/959 16 , exempts emissions covered by a national carbon tax if certain conditions are met. In the view of the Norwegian authorities, an equivalent exemption from national carbon taxes should be allowed.
5 The presence of State aid
5.1 Introduction
(32) Article 61(1) of the EEA Agreement reads as follows: 'Save as otherwise provided in this 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 Contracting Parties, be incompatible with the functioning of this Agreement'.
(33) The qualification of a measure as State aid within the meaning of this provision requires the following cumulative conditions to be met: (i) the measure must be granted by the State or through State resources; (ii) it must confer an advantage on an undertaking; (iii) favour certain undertakings (selectivity); and (iv) threaten to distort competition and affect trade.
(34) As set out in Section 4 above, the Norwegian authorities argue that the measures do not qualify as State aid on the basis that they are not selective within the meaning of Article 61(1) of the EEA Agreement. In its below analyses of the two measures, ESA will therefore first address the question of whether the measures are selective.
5.2 Measure 1
5.2.1 Selectivity
(35) A State measure is selective if it favours certain undertakings or the production of certain goods 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 17 .
(36) The objective pursued by a State measure or the technique used by the State to implement it is not sufficient to exclude the measure from being classified as State aid. Article 61(1) of the EEA Agreement does not distinguish between the causes or objectives of State measures but defines them in relation to their effects 18 .
(37) The selectivity of tax measures is normally assessed by means of a three-step analysis. First, a system of reference is identified. Second, it must be determined whether a given measure constitutes a derogation from that reference system, insofar as it differentiates between economic operators who, in the light of the objectives intrinsic to the system, are in a comparable factual and legal situation. If this question is answered in the affirmative, the measure is prima facie selective. It must then be assessed whether the measure is justified by the nature or general scheme of the system 19 .
5.2.1.1 The reference system
(38) In order to assess the selectivity of a measure under the three-step analysis, it is necessary to first establish the reference system. The reference system amounts to the benchmark against which the selectivity of a measure is assessed 20 .
(39) The reference system is composed of a consistent set of rules that generally apply - on the basis of objective criteria - to all undertakings falling within its scope as defined by its objective 21 . In the case of taxes, the reference system is the normal taxation 22 , based on such elements as the tax base, the taxable persons, the taxable event and the tax rates 23 .
(40) The excise duty on waste incineration is set out in the Norwegian State Budget 24 . The taxable event is the 'emission of fossil CO2 to the air by incineration of waste' 25 . The subjects of the excise duty are waste incinerators 26 . The tax base for the excise duty is based on tonnes of fossil CO2 released through the waste incineration process 27 . Furthermore, the Norwegian authorities explicitly state that the aim of the excise duty is to 'put a price on all [CO2] emissions' 28 . This is to internalise the cost of emitting CO2 to reduce CO2 emissions.
(41) On this basis, the normal taxation under the excise duty on waste incineration appears to be based on the emissions of CO2 from fossil sources into the air through the incineration of waste. This interpretation is corroborated by the fact that incineration of waste which does not contain fossil materials, and incineration where the fossil CO2 is not emitted into the air due to carbon capture and storage, are excluded from the scope of the excise duty 29 .
(2) and section 3-13-6.
(42) Against this background, ESA preliminarily identifies the system of reference as an excise duty on waste incineration activities that release fossil CO2 into the air.
(43) While the Norwegian authorities acknowledge that the reference system against which to assess tax measures is normally the tax itself 30 , they argue that the reference system in this case is narrower than the excise duty on waste incineration. In this regard, the Norwegian authorities have underlined that the duty is only intended to cover emissions from waste incineration causing emissions covered by the ESR.
(44) A similar argument was rejected by ESA in Case No. 342/09/COL 31 . In that case, a general CO2 tax was to be levied on the use of natural gas and LPG. As part of the implementation of this tax, an exception was to be introduced to exempt the use of natural gas and LPG for purposes other than the heating of buildings. The Norwegian authorities argued that this exemption did not constitute a derogation from a general CO2 tax, but rather formed part of the definition of a narrower tax addressing the heating of buildings. ESA was not convinced about this line of argument and pointed out that the measure consisted of a general tax on natural gas and LPG with an exception for use related to activities other than the heating of buildings.
(45) ESA also refers to the judgment rendered by the EFTA Court in Case E-5/04 32 . The background for that case was that the Norwegian authorities had established an exemption from a tax on electricity benefiting the mining and manufacturing industry. In the view of the Norwegian authorities, this did not imply derogating from the normal rule of taxation, but rather that the reference system was limited to the taxation of electricity used for certain purposes. The EFTA Court rejected this argument and stated that:
'[T]he Regulation introduced an exemption from a general rule that electricity consumption is liable to tax. To understand it the way the Applicants do, namely that the Regulation establishes tax liability only for a particular use of electricity, would run counter to the structure of the tax scheme in question and reverse the usual relationship between rule and exemption as confirmed by the explicit use of the term «exemption» in the Regulation' 33 .
(46) In ESA's preliminary assessment, to understand measure 1 as a limited tax on ESR emissions would similarly run counter to the structure of the tax scheme in question.
(47) The Norwegian authorities have further asserted that the excise duty was introduced to fulfil its obligations under the ESR and that it would be illogical if the State aid rules prevent Norway from applying the most cost-efficient measures and force it to impose measures that are wider than necessary under the ESR.
(48) In this respect, ESA acknowledges that it is up to the national authorities to design and implement the instruments ensuring compliance with their obligations pursuant to the ESR. The instruments relied on must, however, comply with the EEA Agreement, including its Article 61(1). It follows from consistent case-law that the objective pursued by a measure is normally not sufficient to exclude its classification as State aid 34 .
5.2.1.2 Derogation from the reference system
(49) In the second step, it must be assessed whether measure 1 differentiates between undertakings in derogation from the reference system. To determine this, it is necessary to establish whether the measure is liable to favour certain undertakings, or the production of certain goods, compared with other undertakings which are in a similar factual and legal situation in the light of the intrinsic objective of the reference system 35 .
(50) The structure of special-purpose levies, such as environmental taxes imposed to discourage activities that have an adverse effect on the environment, will normally integrate the policy objective pursued 36 . As reflected in point(40) above, ESA's current understanding is that the objective intrinsic to the reference system is to 'put a price on all CO2 emissions' from waste incineration so that the environmental costs of each unit of CO2 emitted is internalised at least at the level set by the excise duty.
(51) The Norwegian authorities however contend that there is no derogation from the reference system as the exempted activities are covered by the ETS 37 . As the ETS imposes costs on undertakings by virtue of the obligation to surrender emissions allowances, the Norwegian authorities argue that undertakings are in a different legal and factual situation with respect to their waste incineration emissions covered by the ETS than activities which are not covered by the ETS.
(52) Based on the relatively limited information submitted by the Norwegian authorities, ESA currently questions whether undertakings can be deemed to be in a different factual or legal situation depending simply on whether their emissions are covered by the ESR or the ETS. In this regard, ESA recalls that the ETS is a regulatory, non-tax system, which may function differently to a tax. The Norwegian authorities have furthermore not elaborated to what extent waste incinerators can be expected to incur additional costs as a result of being subject to the ETS.
(53) In its Decision 2009/972/EC, the Commission assessed a Danish measure, which introduced exemptions from the CO2 tax paid by energy consumers in Denmark. The effect of the proposed exemptions would be to exclude emissions subject to the ETS from the tax. In its assessment, the Commission found that, with respect to the CO2 tax, undertakings were not in different legal and factual situations simply depending on whether their activities were subject to the ETS 38 .
(54) In view of the above, ESA takes the preliminary view that measure 1 may be prima facie selective insofar as it simply excludes waste incineration that produces CO2 emissions which are subject to the ETS from the excise duty on waste incineration.
5.2.1.3 Justification by the nature or general scheme of the system of reference
(55) A measure which is prima facie selective is nevertheless to be considered non-selective if it is justified by the nature or general scheme of the reference system. This is the case where a measure derives directly from the intrinsic basic or guiding principles of the reference system, or where it is the result of inherent mechanisms necessary for the functioning and effectiveness of that system 39 .
(56) The Norwegian authorities have argued that measure 1 is justified by the general nature and logic of the reference system as the exemption will ensure that double regulation is avoided. In the view of the Norwegian authorities, the measure will ensure that waste incinerators do not have to internalise the environmental costs of their CO2 emissions subject to the ETS twice.
(57) As has been set out above, however, it is ESA's preliminary view that with respect to measure 1, the system of reference is the excise duty on waste incineration of fossil materials emitting CO2 into the air. Moreover, in ESA's preliminary understanding, the intrinsic objective and logic of this reference system is to introduce an excise duty on waste incineration to ensure that the environmental costs of each unit of CO2 emitted from waste incineration is internalised at least at the level set by this excise duty. Consequently, since it does not reflect the extent to which waste incinerators actually incur additional costs, as a result of the ETS, the proposed exemption to be introduced by measure 1 does not appear to be in line with this logic.
(58) This finding is consistent with that made by the Commission in the case concerning the Danish exemptions from the CO2 tax paid by energy consumers in Denmark 40 .
(59) The Norwegian authorities have additionally referred to the exemption from ETS 2 contained in Article 30(e)(3) of the ETS Directive, as amended by Directive 2023/959. The exemption, in essence, allows for the obligation under the ETS 2 to surrender emission allowances to be waived for undertakings that pay a national carbon tax which exceeds the average price for such allowances. In the view of the Norwegian authorities, national authorities should be allowed to establish corresponding exemptions in their national carbon taxes.
(60) In this regard, ESA notes that the exemption in Article 30(e)(3) of the ETS Directive is specific to the ETS 2 and that its duration is limited to the end of 2030.
5.2.2 Remaining criteria
(61) According to Article 61(1) of the EEA Agreement, a measure must be imputable to the State and be granted through State resources to qualify as State aid. Measure 1 satisfies these conditions as it comprises an exemption from the excise duty on waste incineration that will result in a loss of State revenue compared with the situation where no such exemption had been established.
(62) By providing for an exemption from the excise duty that would otherwise be due for waste incinerators subject to the ETS, measure 1 also constitutes a relief from economic burdens the beneficiaries would have to bear if not for the measure. In light of the above assessment under the three-step analysis, ESA cannot exclude that this advantage is selective in nature.
(63) The Norwegian authorities have furthermore not submitted information indicating that the beneficiaries are only active on markets where there is no or limited competition and trade between the Contracting Parties to the EEA Agreement. To the contrary, it is ESA's preliminarily understanding that the treatment of waste is subject to competition and trade within the EEA. Based on this, ESA takes the preliminary view that measure 1 is liable to distort competition and affect trade between the Contracting Parties to the EEA Agreement.
(64) Based on the above, ESA preliminarily concludes that measure 1 may fulfil all of the conditions in Article 61(1) of the EEA Agreement.
5.3 Measure 2
5.3.1 Selectivity
5.3.1.1 The reference system
(65) The CO2 tax on mineral products is imposed on mineral oil, petroleum, natural gas and LPG 41 . According to the Norwegian authorities, it aims to 'put a price on all CO2 emissions' to internalise the cost of emitting CO242 . Different metrics (Sm3 and kgs) are used for the purposes of calculating the tax for different products. This ensures that the general tax rate applied across products equals approximately NOK 1 176 per tonnes of CO2 emitted 43 . There are certain conditions that may lead to a reduced tax rate, but ESA cannot see that any of these are relevant for the delimitation of the reference system.
(66) In view of the above, ESA takes the preliminary view that the normal taxation under the reference system is the levying of a CO2 tax on mineral products leading to emissions of CO2. This tax appears to be levied based on the CO2 emitted from the mineral products upon use. In line with this, mineral products used for industrial activities which are associated with no or significantly reduced CO2 emissions, as well as for activities were the emissions are captured and stored, are exempted from the tax 44 . The fact that measure 2 is explicitly incorporated as an exemption from the CO2 tax on mineral products further confirms that it forms part of the same reference system as this tax 45 .
(67) Following the same line of reasoning as for measure 1, the Norwegian authorities argue that the reference system for measure 2 is not the CO2 tax on mineral products, but instead a CO2 tax for mineral products causing emissions covered by the ESR. As follows from the above, ESA currently questions this position. ESA furthermore refers to the reasoning set out in the above paragraphs(44) to(46), which is equally valid with respect to measure 2. In this respect, ESA also recalls that in the context of the case assessed in ESA Decision No 342/09/COL, the Norwegian authorities had argued that an exemption to the CO2 tax on natural gas and LPG made up the reference system. ESA however found that the system of reference constituted 'all sectors and undertakings subject to the CO2 tax, meaning those who consume or produce mineral oils, petroleum, LPG or natural gas' 46 .
(68) In view of the above, ESA preliminarily identifies the system of reference as the CO2 tax on mineral products.
5.3.1.2 Derogation from the reference system
(69) In the same way as for measure 1, the Norwegian authorities contend that there is no derogation from the reference system as exempted undertakings are covered by the ETS. In the view of the Norwegian authorities, this puts them in a different legal and factual situation than non-exempted undertakings.
(70) However, the structure and stated purpose of the CO2 tax on mineral products, as identified in paragraphs(65) to(66) above, would seem to suggest that its intrinsic objective is to impose the cost level set by this tax on emissions of CO2 to the air from mineral products. Given this, the fact that an activity falls within the scope of the ETS does not appear sufficient in itself to conclude that an undertaking is in a different legal and factual situation than undertakings with emissions encompassed by the ESR. As was noted in paragraph 52 above with respect to measure 1, the ETS is a regulatory, non-tax system which may function differently to a tax. The Norwegian authorities have furthermore not elaborated to what extent the concerned emitters can be expected to incur additional costs as a result of being subject to the ETS.
(71) In view of these considerations, ESA takes the preliminary view that measure 2 may be prima facie selective insofar as it simply excludes activities, which are subject to the ETS from the CO2 tax on mineral products.
5.3.1.3 Justification by the nature or general scheme of the reference system
(72) The Norwegian authorities have also argued that measure 2 is justified by the general nature and logic of the reference system as it will ensure that double regulation is avoided.
(73) However, as has been set out above, the system of reference in this case appears to be the CO2 tax on mineral products. In ESA's preliminary understanding, the intrinsic objective and logic of this reference system is to ensure that the environmental costs of each unit of CO2 emitted is internalised at least at the level set by this tax. Consequently, since it does not reflect the extent to which emitters actually incur additional costs as a result of the ETS, the proposed exemption to be introduced by measure 2 does not appear to be in line with this logic.
5.3.2 Remaining criteria
(74) The reasoning set out in the above Section 5.2.2 is equally valid with respect to measure 2. This measure therefore appears to fulfil the remaining conditions in Article 61(1) of the EEA Agreement.
5.4 Preliminary view
(75) In light of the above, ESA's preliminary view is that measures 1 and 2 may qualify as State aid, as defined in Article 61(1) of the EEA Agreement.
6 Aid scheme or individual aid
(76) ESA notes that the legal basis of the measures is an act which does not require further implementing measures for the granting of the aid, and which identifies the beneficiaries in a general and abstract manner 47 . The aid therefore appears to be granted on the basis of an aid scheme.
7 Lawfulness of the aid
(77) Pursuant to Article 1(3) of Part I of Protocol 3: 'The EFTA Surveillance Authority shall be informed, in sufficient time to enable it to submit its comments, of any plans to grant or alter aid. [...] The State concerned shall not put its proposed measures into effect until the procedure has resulted in a final decision.'
(78) The Norwegian authorities notified the measures on 29 February 2024 and have yet to let them enter into force. They have therefore complied with their obligations under Article 1(3) of Part I of Protocol 3.
8 Compatibility of the measures
8.1 Introduction
(79) The burden of proving the compatibility of aid with the functioning of the EEA Agreement, under one of its derogations from Article 61(1) of the EEA Agreement, is borne by the EFTA State concerned. Consequently, it is for the national authorities to establish that the conditions for the derogation they are invoking are satisfied 48 .
(80) In their notification, the Norwegian authorities have not discharged this burden of proof by substantiating that the measures comply with one of the derogations from the State aid prohibition. ESA therefore has doubts concerning whether the measures are compatible with the functioning of the EEA Agreement. In order to facilitate for the Norwegian authorities and other interested parties to comment on this issue, ESA will nevertheless identify the potential grounds for compatibility that may be applicable. ESA will also identify conditions under these compatibility grounds where it currently has doubts as to whether the conditions are fulfilled in the case at hand.
(81) Article 61(2) of the EEA Agreement is not applicable to the measures, as they do not have a social character, do not make good the damage caused by natural disasters or exceptional occurrences, and are not directed at certain areas of the economy of the Federal German Republic. Furthermore, the aid cannot be justified under Article 61(3)(a) of the EEA Agreement, as the aid does not promote the economic development of areas where the standard of living is abnormally low or where there is serious underemployment. Equally, since it is evident that the measures do not promote the execution of an important project of common European interest or remedy a serious disturbance in the Norwegian economy, Article 61(3)(b) of the EEA Agreement is not applicable.
(82) Article 61(3)(c) of the EEA Agreement provides that ESA may declare compatible 'aid to facilitate the development of certain economic activities or of certain economic areas, where such aid does not adversely affect trading conditions to an extent contrary to the common interest'. Therefore, in order to declare State aid compatible on the basis of this provision, the aid must firstly facilitate the development of certain economic activities or of certain economic areas. Secondly, the aid must not adversely affect trading conditions to an extent contrary to the common interest 49 .
(83) In its Guidelines on State aid for climate, environmental protection and energy ('CEEAG') 50 , ESA has set out conditions according to which aid measures in respect of environmental protection and energy will be declared compatible with the EEA Agreement pursuant to its Article 61(3)(c).
(84) As has already been explained, the notified measures aim to facilitate the development of economic activities in a manner that improves environmental protection. In view of this stated objective, ESA considers it appropriate to address below the question of whether the measures comply with CEEAG. In the continuation of this assessment, ESA will also provide its preliminary assessment of whether the measures may comply with the corresponding provisions in the General Block Exemption Regulation ('the GBER') 51 .
(85) Lastly, ESA will address the issue of whether the measures can be declared compatible with the functioning of the EEA Agreement on the basis of an assessment directly under its Article 61(3)(c).
8.2 Assessment against CEEAG
8.2.1 Scope and supported activities
8.2.1.1 Measure 1
(86) As explained in paragraphs 293-294 of the CEEAG, while reductions in environmental taxes may adversely impact the environmental objectives promoted by the tax, the reductions may nonetheless be needed where the beneficiaries would otherwise be placed at such a competitive disadvantage that it would not be feasible to introduce the environmental tax in the first place. Thus, reductions in environmental taxes and levies may be compatible provided that it at least indirectly contributes to an improvement of the level of environmental protection and that the tax reduction does not undermine the general objective of the tax.
(87) According to paragraph 295 of the CEEAG, aid in the form of tax or levy reductions may be compatible if:
a) the reductions are targeted at the undertakings most affected by the environmental tax or levy that would not be able to pursue their economic activities in a sustainable manner without the reduction and
b) the level of environmental protection actually achieved by implementing the reductions is higher than the one that would be achieved without the implementation.
(88) In ESA's preliminary understanding, the measure facilitates the economic activity of waste incineration pursued by undertakings subject to the ETS. In the absence of the measure, undertakings may have to bear the costs associated with surrendering emissions allowances under the ETS, as well as the excise duty on waste incineration.
(89) However, it is not evident to ESA that measure 1 is targeted at undertakings that would not be able to pursue their economic activities in a sustainable manner without the reduction. In this regard, ESA notes that a number of emissions allowances are allocated free of charge pursuant to the ETS. Based on this, it is also not evident that the level of environmental protection would be increased by implementing the measure, as no mechanism to ensure that exemptions would only be granted to undertakings that have net costs from the ETS participation is in place.
8.2.1.2 Measure 2
(90) In ESA's preliminary assessment, a line of reasoning corresponding to that set out in Section 8.2.1.1 is also applicable with respect to measure 2.
8.2.2 The necessity and proportionality of the aid
8.2.2.1 Measure 1
(91) As reiterated in paragraph 300 of the CEEAG, an in-depth assessment of the necessity and proportionality of the aid is needed when environmental taxes are not harmonised at EEA-level. On this basis, it is ESA's preliminary assessment that the Norwegian authorities must carry out an in-depth assessment in accordance with Sections 4.7.1.3.1 to 4.7.1.3.3 of the CEEAG, in order to demonstrate the necessity and proportionality of the aid.
(92) In this regard, ESA notes that the Norwegian authorities have not presented information allowing ESA to assess the necessity of the aid under paragraph 302 of the CEEAG. Equally, the Norwegian authorities have not presented information addressing the assessment of the appropriateness of the measure under Section 3.2.1.2 and paragraphs 305-306 of the CEEAG.
(93) As concerns the assessment of the proportionality of the aid under Section 3.2.1.3 of the CEEAG, ESA notes in addition that it follows from paragraph 308 of the CEEAG that ESA will consider aid to be proportionate if each beneficiary pays at least 20% of the nominal amount of the environmental tax or parafiscal levy that would be applicable to that beneficiary in the absence of the reduction.
(94) In ESA's preliminary assessment, the wording of paragraph 308 of the CEEAG supports that each beneficiary must pay a sufficient proportion of the environmental tax that would be applicable in the absence of the reduction in order for the aid to qualify as proportionate. Under such an interpretation, other costs borne by the concerned beneficiaries, such as costs associated with the ETS, are immaterial for the assessment against the 20%-threshold in paragraph 308 of the CEEAG.
(95) This interpretation is, in ESA's preliminary assessment, supported by the judgment of the General Court in Joined Cases T-129/07 and T-130/07. In those cases, a beneficiary contended that the Commission had failed to take into account the onerous environmental obligations to which it was subjected, including the ETS, when assessing whether the beneficiary paid a 'significant proportion' of the concerned national environmental tax 52 . This line of argument was rejected by the General Court on the basis that the Commission was not under an obligation to rectify alleged distortive effects resulting from the differences between various national tax regimes.
(96) In any event, a number of emissions allowances are, as already mentioned, allocated free of charge pursuant to the ETS. Therefore, it cannot merely be presumed that the measure will exclusively benefit beneficiaries which are purchasing emissions allowances at market rates to cover their emissions.
8.2.2.2 Measure 2
(97) In ESA's preliminary assessment, the line of reasoning set out in Section 8.2.2.1 is equally applicable with respect to measure 2.
8.3 Article 44a GBER
(98) Pursuant to Article 3 GBER, aid measures shall be compatible with the EEA Agreement and exempted from the notification requirement provided that such aid fulfils all the conditions laid down in Chapter I GBER, as well as the specific conditions for the relevant category of aid laid down in Chapter III GBER.
(99) Article 44a GBER concerns aid in the form of reductions in environmental taxes or parafiscal levies. The material conditions under this provision are generally similar to those found in the corresponding paragraphs of CEEAG. Paragraphs two and three of Article 44a GBER correspond to paragraph 295 of the CEEAG. Paragraph five of Article 44a GBER corresponds to paragraph 308 of the CEEAG. The material assessments made in regard to the conditions of the CEEAG in Sections 8.2.2.1 and 8.2.2.2 above are therefore equally relevant under Article 44a GBER.
(100) It consequently follows from the above assessments that, in ESA's preliminary view, the measures do not comply with Article 44a GBER.
8.4 Assessment directly under Article 61(3)(c) of the EEA Agreement
(101) As follows from the above, ESA doubts whether the measures comply with the applicable conditions that have been set out in the CEEAG and GBER pursuant with Article 61(3)(c) of the EEA Agreement. The Norwegian authorities have also not submitted any information capable of establishing that the conditions for approving the measures, by applying Article 61(3)(c) of the EEA Agreement directly, are satisfied.
9 Conclusion
(102) As set out above, ESA preliminarily considers that measures 1 and 2 may constitute State aid within the meaning of Article 61(1) of the EEA Agreement. Provided that the measures qualify as State aid, ESA furthermore doubts whether the measures would be compatible with the functioning of the EEA Agreement.
(103) Consequently, and in accordance with Article 4(4) of Part II of Protocol 3, ESA hereby opens the formal investigation procedure provided for in Article 1(2) of Part I of Protocol 3. The decision to open a formal investigation procedure is without prejudice to the final decision of ESA, which may conclude that measures 1 and 2 do not constitute State aid, or that they amount to aid measures which are compatible with the functioning of the EEA Agreement.
(104) ESA, acting under the procedure laid down in Article 1(2) of Part I of Protocol 3, invites the Norwegian authorities to submit their comments by 2 May 2024, and to provide all documents, information and data needed for the assessment of the measures in light of the State aid rules.
(105) The Norwegian authorities have confirmed that this opening decision does not contain any business secrets or other confidential information that should not be published.
(106) Finally, ESA will inform interested parties by publishing a meaningful summary in the Official Journal of the European Union and the EEA Supplement thereto. All interested parties will be invited to submit their comments within one month of the date of such publication. The comments will be communicated to the Norwegian authorities.
Done in Brussels,
For the EFTA Surveillance Authority,
Arne R0KSUND Stefan BARRIGA
President College Member
Responsible College Member
Árni Páll ÁRNASON For Melpo-Menie JOSÉPHIDES
College Member Countersigning as Director,
Legal and Executive Affairs
1 Document Nos 1439561, 1439563 and 1439565.
2 Prop. 1 LS (2021-2022), Skatter, avgifter og toll 2022, item 9.9.5.
3 LOV-2004-12-17-9.
4 Directive 2003/87/EC of the European Parliament and of the Council of 13 October 2003 establishing a scheme for greenhouse gas emission allowance trading within the Community and amending Council Directive 96/61/EC, OJ L 275, 25.10.2003, pp. 32-46, act referred to at point 21al of Annex XX to the EEA Agreement, as amended.
5 The general tax rate on waste incineration is currently NOK 882 per tonnes of CO2. Activities subject to the Climate Quota Act are levied a reduced rate of NOK 176 per tonnes of CO2, constituting 20 per cent of the general tax rate, see GBER 11/2024/ENV.
6 Prop. 1 LS (2021-2022), Skatter, avgifter og toll 2022, Proposal for Parliamentary decision p. 333.
7 Regulation (EU) 2021/1119 of the European Parliament and of the Council of 30 June 2021 establishing the framework for achieving climate neutrality and amending Regulations (EC) No 401/2009 and (EU) 2018/1999 ('European Climate Law'), OJ L 243, 9.7.2021, pp. 1-17. The European Climate Law has been considered not to be relevant for incorporation into the EEA Agreement.
8 See the EEA Joint Committee Decision No 269/2019 of 25 October 2019 and the declarations made in conjunction with this decision, OJ L 11, 12.1.2023, pp. 38-45. See also the press release of the European Commission of 25 October 2019.
9 Regulation (EU) 2018/842 of the European Parliament and of the Council of the European Union of 30 May 2018 on binding annual greenhouse gas emission reductions by Member States from 2021 to 2030 contributing to climate action to meet commitments under the Paris Agreement and amending Regulation (EU) No 525/2013 ('Effort Sharing Regulation'), OJ L 156, 19.6.2018, pp. 26-42, act referred to at Article 8(a), second indent, of Protocol 31 to the EEA Agreement.
10 Regulation (EU) 2018/841 of the European Parliament and of the Council of 30 May 2018 on the inclusion of greenhouse gas emissions and removals from land use, land use change and forestry in the 2030 climate and energy framework, and amending Regulation (EU) No 525/2013 and Decision No 529/2013/EU, OJ L 156, 19.6.2018, pp. 1-25, act referred to at Article 8(a), first indent, of Protocol 31 to the EEA Agreement.
12 Decision of the EEA Joint Committee No 146/2007 of 26 October 2007 amending Annex XX (Environment) to the EEA Agreement, OJ L 100, 10.4.2008, pp. 92-98.
13 Directive (EU) 2023/959 of the European Parliament and of the Council of 10 May 2023 amending Directive 2003/87/EC establishing a system for greenhouse gas emission allowance trading within the Union and Decision (EU) 2015/1814 concerning the establishment and operation of a market stability reserve for the Union greenhouse gas emission trading system, OJ L 130, 16.5.2023, pp. 134-202, act referred to at point 21al of Annex XX to the EEA Agreement.
14 The notification, first paragraph.
15 ESA's Guidelines on the notion of State aid as referred to in Article 61(1) of the EEA Agreement ('NoA') (OJ L 342, 21.12.2017, p. 35), paragraph 134.
16 Ibid.
17 Judgment of the Court of Justice of 8 November 2001, Adria-Wien Pipeline, C-143/99, EU:C:2001:598, paragraph 41.
18 Judgment of the Court of Justice of 22 December 2008, British Aggregates v Commission, C-487/06 P, EU:C:2008:757, paragraphs 81-89.
19 NoA, paragraph 128.
20 NoA, paragraph 132.
21 NoA, paragraph 133.
22 Judgment of the Court of Justice of 6 September 2006, Portugal v Commission, C-88/03, EU: C:2006:511, paragraph 56.
23 NoA, paragraph 133.
24 Prop. 1 LS (2023-2024) Skatter og avgifter 2024, item 23-8-7.
25 Regulation of 11 December 2001 No. 1451 on excise duties, FOR-2001-12-11-1451, section 3-13-1.
26 Ibid. Section 3-13-2.
27 Ibid. Section 3-13-4.
28 The notification, section 3.
29 See footnote 22, section 3-13-1
30 NoA, paragraph 134.
31 ESA Decision No 342/09/COL of 23 July 2009 on an exemption from the Norwegian CO2 tax on gas and LPG on the use of gas for purposes other than the heating of buildings, OJ L 226, 1.9.2011, pp. 12-19.
32 E-5/04 Fesil ASA and Finnfjord Smelteverk AS v EFTA Surveillance Authority, Judgment of 21 July 2005, OJ C 45, 23.2.2006, p. 14.
33 Ibid. Paragraph 79.
34 Judgment of the Court of Justice of 22 December 2008, British Aggregates v Commission, C-487/06 P, EU:C:2008:757, paragraph 84.
35 NoA, paragraph 135.
36 NoA, paragraph 136.
37 Through obligations subject to the Climate Quota Act.
38 Commission Decision of 17 June 2009 on aid scheme C 41/06 (ex N 318/A/04) which Denmark is planning to implement for refunding the CO2 tax on quota-regulated fuel consumption in industry, OJ L 345, 23.12.2009, pp. 18-27, paragraph 41.
39 NoA, paragraph 138.
40 Paragraph 44 of the decision.
41 See footnote 25, section 3-6-1.
42 The notification, section 3.
43 The notification, section 3.
44 See footnote 24, section 23-8-5 B, § 2 letter f and g.
45 Measure 2 formally consists of both introducing a tax on the processing industry and exempting undertakings subject to the ETS from the tax.
46 See footnote 31.
47 See Article 1(d) of Part II of Protocol 3 to The Agreement between the EFTA States on the Establishment of a Surveillance Authority and a Court of Justice ('Protocol 3').
48 Judgment of the Court of First Instance of 12 September 2007, Olympiaki Aeroporia Ypiresies v Commission, T-68/03, EU:T:2007:253, paragraph 34; Judgment of the General Court of 17 July 2014, Westfalisch-Lippischer Sparkassen- und Giroverband v Commission. T-457/ 09, EU:T:2014:683, paragraph 295.
49 Judgment of the Court (Grand Chamber) of 22 September 2020, Austria v Commission (Hinkley Point C), C-594/18 P, EU:C:2020:742, paragraphs 18-20.
50 The CEEAG was published in the OJ L 277, 27.10.2022, p. 218.
51 Commission Regulation (EU) No 651/2014 of 17 June 2014 declaring certain categories of aid compatible with the internal market in application of Articles 107 and 108 of the Treaty (OJ L 187, 26.6.2014, p. 1), referred to at point 1j of Annex XV to the EEA Agreement, as amended.
52 Community guidelines on State aid for environmental protection (2001/C 37/03) (OJ C 37, 3.2.2001, pp. 3-15).
