Posts Tagged Renewable energy
In C‑212/18 Prato Nevoso Termo Energy the CJEU held on the not always straightforward concurrent application of the Waste Framework Directive (WFD) 98/2008 and the various Directives encouraging the uptake of renewable energy. It referred i.a. to the circular economy and to precaution.
On the face of it the economic and environmental benefits of the case may seem straightforward. Prato Nevoso operates a power plant for the production of thermal energy and electricity. It applied for authorisation to replace methane as the power source for its plant with a bioliquid, in this case a vegetable oil produced by ALSO Srl, derived from the collection and chemical treatment of used cooking oils, residues from the refining of vegetable oils and residues from the washing of the tanks in which those oils were stored. ALSO has a permit to market that oil as an ‘end-of-waste’ product within the meaning of relevant Italian law , for use in connection with the production of biodiesel, on condition that it has the physico-chemical characteristics indicated in that permit and that the commercial documents indicate ‘produced from recovered waste for use in biodiesel production’.
Prato Nevoso was refused the requested authorisation on the ground that the vegetable oil was not included in a relevant Italian list, which sets out the categories of biomass fuels that can be used in an installation producing atmospheric emissions without having to comply with the rules on the energy recovery of waste. The only vegetable oils in those categories are those from dedicated crops or produced by means of exclusively mechanical processes.
The argument subsequently brought was that the refusal violates Article 6 WFD’s rules on end-of-waste, and Article 13 of the RES Directive 2009/28. That Article essentially obliges the Member States to design administrative procedures in such a way as to support the roll-out of renewable energy.
The CJEU first of all refers to its finding in Tallina Vesi that Article 6(4) of Directive 2008/98 does not, in principle, allow a waste holder to demand the recognition of end-of-waste (EOW) status by the competent authority of the Member State or by a court of that Member State. MSs have a lot of flexibility in administering EOW in the absence of European standards. That the use of a substance derived from waste as a fuel in a plant producing atmospheric emissions is subject to the national legislation on energy recovery from waste, is therefore entirely possible (at 39). A13 of the RES Directive has no impact on that reality: that Article does not concern the regulatory procedures for the adoption of end-of-waste status criteria.
Nevertheless, the MS’ implementation of the RES Directives must not endanger the attainment of the WFD, including encouragement of the circular economy etc. and likewise, the WFD’s waste hierarchy has an impact on the RES’ objectives. A manifest error of assessment in relation to the non-compliance with the conditions set out in Article 6(1) of Directive 2008/98 could be found to be a MS violation of the Directive.
At 43: ‘It is necessary, in this case, to examine whether the Member State could, without making such an error, consider that it has not been demonstrated that the use of the vegetable oil at issue in the main proceedings, in such circumstances, allows the conclusion that the conditions laid down in that provision are met and, in particular, that that use is devoid of any possible adverse impact on the environment and human health.’ At 44: ‘It is for the national court, which alone has jurisdiction to establish and assess the facts, to determine whether that is the case in the main proceedings and, in particular, to verify that the non-inclusion of those vegetable oils in the list of authorised fuels results from a justified application of the precautionary principle.’
At 45 ff the CJEU does give a number of indications to the national judge, suggesting that no such infringement of the precautionary principle has occurred (including the reality that specific treatment and specific uses envisaged of the waste streams, has an impact on their environmental and public health safety). At 57: It must be considered that the existence of a certain degree of scientific uncertainty regarding the environmental risks associated with a substance — such as the oils at issue in the main proceedings — ceasing to have waste status, may lead a Member State, taking into account the precautionary principle, to decide not to include that substance on the list of authorised fuels’.
An important judgment.
Handbook of EU Waste law, 2nd ed. 2015, OUP, 1.166 ff and 1.189 ff.
Saugmandsgaard ØE in C-634/17 ReFood. The animal by-products exemption in the EU’s waste shipments Regulation. (Renewable energy claxon).
Update 25 May 2019. The CJEU agrees with its AG. The animal by-products exemption has broad calling (and no prior certification of the nature of these by-products is required prior to their transborder shipment).
This post requires seriously engaged interest in EU waste law. Very few of you I am sure are familiar with my work – in Dutch (with Tom de Gendt, and Kurt Deketelaere) on animal waste /animal by-products. Yet please all those of you who are not waste nerds, do not turn away yet: for animal wastes and animal by-products are a raw material for biogas installations. The regulatory issues at stake therefore are relevant to the renewable energy sector.
Saugmandsgaard ØE opined end January in C-634/17 ReFood – the English text was not available at the time of writing. A lorry with animal by-products collected in The Netherlands, was making its way to a German biogas installation (one of many many thousands such transports) when it was stopped, the driver being asked to produce the relevant waste export permit – which he did not possess.
Recital 11 of the waste shipments Regulation 1013/2006, introduces the issue at stake, which is avoiding regulatory duplication: ‘It is necessary to avoid duplication with Regulation (EC) No 1774/2002 of the European Parliament and of the Council of 3 October 2002 laying down health rules concerning animal by-products not intended for human consumption, which already contains provisions covering the overall consignment, channelling and movement (collection, transport, handling, processing, use, recovery or disposal, record keeping, accompanying documents and traceability) of animal by-products within, into and out of the Community.’ As a result, the Regulation exempts from its scope of application ‘shipments which are subject to the approval requirements of Regulation (EC) No 1774/2002’. Core of the regulatory conundrum is that Regulation 1774/2002 does not contain ‘approval requirements’ for the relevant category. (They are category 3 animal by-products, these are the least problematic animal wastes).
The AG suggests a broad reading of the exemption, and one which prevents overlap between the two regimes. Animal by-products fall under the exemption full stop: there are no two, three or more ways about it. (The AG argues along the lines of linguistic analysis, regulatory logic, and the preparatory works of all EU secondary law at issue).
Thank you Jonathan Cocker for flagging Ontario’s stakeholder consultation on renewable fuel standards, aka biofuels. Current thinking, outlined in the discussion paper, is to make the standards ‘performance based’: ie without pushing one or rather additive and exclusively focus on achieved (documented) reduction of greenhouse gas emissions.
Biofuels are known to create international trade tension. Argentina and the EU are still formally in consultation over the EU’s approach. Various WTO dispute settlement concerns anti-dumping duties on biofuels. Finally one or two elements of WTO dispute settlement on support for renewable energy touch upon fuel standards.
With all that in mind one particular element of the Ontario regime caught my attention: the intention to regulate GHG emissions ‘well to wheel’: ie ‘to assess emissions performance across the fuel’s full well-to-wheel lifecycle, from extraction to processing, distribution and end-use combustion.’(p.6). Canada does that already for diesel, with its 2014 greener diesel Regulation, employing what is known as the ‘GHGenius’ model.
What I have not been able to gauge from my admittedly limited research into that model: does it at all and if so how, apply to particularly extraction outside of Canada indeed outside Ontario? For the EU, much of the biofuel production (let alone biofuel imports) at some point or another involves extra-EU elements. How does a well to wheel method in such case work under WTO rules?
Essent 2.0. The CJEU surprisingly does distinguish. Support for renewable, ‘green’ energy not entirely carte blanche.
Excuse the attempt at pun in the title (which readers may have even missed. ‘Green’ v carte ‘Blanche’. It’s Thursday, and these are busy weeks). Apologies also to the readers who are new to the debate. The legality of support schemes for renewable energy EU law has occupied mine and others’ mind for a little while now. One may want to refer eg to my paper on the Vindkraft et al judgment or to various postings on this blog. Specifically, for the latter, my post on the AG’s Opinion in Essent 2.0, case C-492/14., judgment issued today.
Bot AG had opined, very very reluctantly, that the Court’s case-law meant that Flanders could indeed reserve the benefit of the free distribution of electricity produced from renewable energy sources solely to generating installations directly connected to the distribution systems located in Flanders, thereby excluding generating installations located in other Member States.
The Court itself has now distinguished its own case-law: the EU has not harmonised the national support schemes for green electricity; this means that it is possible in principle for Member States to limit access to such schemes to green electricity production located in their territory. However the Court’s sympathy is now limited to schemes that support producers only. Green energy support schemes, whose production costs seem to be still quite high as compared with the costs of electricity produced from non-renewable energy sources, are inherently designed in particular to foster, from a long-term perspective, investment in new installations, by giving producers certain guarantees about the future marketing of their green electricity (at 110, with reference to Vindkraft).
However it is not the purpose of the Flemish scheme to give direct support to producers of green electricity. Rather, the free distribution of green electricity constitutes a financial advantage conferred primarily on the supplier of such electricity, which may, in certain circumstances, depending notably on the sale price which the consumer is charged by the supplier for his electricity, to a certain extent and indirectly also benefit the consumer (at 112).
Such a support mechanism offers no certainty that the economic advantage thus obtained for suppliers will ultimately actually and essentially be required to benefit producers of green electricity, particularly the smallest local generating installations which the Flemish Region claims to have wanted to support, which are not both producers and suppliers (at 113).
The Court is not game to assist the AG with his call for an explicit recognition of the potential to use discriminatory measures within the context of mandatory requirements (the implications of Cassis de Dijon). That is a pity, but not a surprise.
Overall, the Court’s judgment is a welcome safeguard to its more open-ended sympathy for renewable energy support schemes. Those who challenge such schemes in future, know what to do. They need to show that there is no certainty that the economic advantage obtained for suppliers will ultimately actually and essentially be required to benefit producers of green electricity, as opposed to distributors or consumers.
Next-up: a reversal of T-351/02 Deutsche Bahn?
Know your biomass from your biomass! The ECJ allows less favourable treatment of wood and wood waste in Industrie du bois de Vielsalm
In Industrie du bois de Vielsalm, Case C-195/12, the ECJ yesterday held in favour of the Walloon Region of Belgium, finding that a regional support scheme providing for the grant of ‘green certificates’ to cogeneration plants, which grants a larger number of green certificates to cogeneration plants processing principally forms of biomass other than wood or wood waste, does not infringe the principle of equality and non-discrimination.
The Court found first of all that Directive 2004/8 on the promotion of co-generation does not exhaustively regulate national support schemes for cogeneration and electricity production from renewable energy sources: Member States are given wide discretion.
It then argued that there are sound environmental reasons for discriminating against wood and wood waste in co-generation support schemes:
‘ (…) even at the level of the renewable nature of the resource, and hence from the point of view of its availability, as also from the point of view of sustainable development, prudent and rational utilisation of natural resources, and security of supply, wood, which is a resource whose renewal requires a long period, may be distinguished from agricultural products or household and industrial waste, whose production takes place in a much shorter space of time. (at 74)
‘Furthermore, it is common ground that the overall environmental impact produced by the increased use of biomass for energy production likely to follow from support measures differs according to the particular characteristics of the type of biomass used. As regards the environmental impact that could follow from enhanced support measures for the use of wood and/or wood waste for energy production, it may thus prove necessary to take into account that any excessive or premature deforestation which may be encouraged by such support measures is liable to contribute to an increased presence of carbon dioxide in the atmosphere and adverse effects on biodiversity or water quality.
Increased development of agricultural products intended for energy production is liable for its part to increase various forms of pollution specifically linked with agricultural activities, in particular with the use of fertilisers and pesticides, such as adverse effects on the water supply. (at 75 ff)
‘Finally, factors such as the quantities in which the various renewable energy sources are present in the territory of the Member State concerned, or the level of development that may already have been achieved there as regards recourse to one or other renewable energy source for cogeneration or electricity production, are also capable of influencing the choices to be made with respect to the renewable energy sources to be promoted in that Member State for the purposes of environmental protection and security and diversification of the energy supply. (at 79)
‘Having regard to all the foregoing, it must be considered that, in the light in particular of the objectives pursued by Directives 2001/77 and 2004/8 and the aims of the European Union in the field of the environment, and of the broad margin of discretion allowed to the Member States by those directives for the adoption and implementation of support schemes intended to promote cogeneration and electricity production from renewable energy sources, and having regard to the individual characteristics of the various categories of biomass capable of use in a cogeneration process, those categories must not be regarded in the context of such support schemes as being in a comparable situation for the purposes of the possible application of the principle of equal treatment, observance of which is ensured by European Union law.
The need to be able to treat those various categories of biomass differently and, in particular, in the light of various environmental considerations, to make choices as to the types of substances to benefit from support and to draw distinctions as regards the specific details of that support, including the amount of the support, must on the contrary be regarded as inherent in that context, without it being possible to consider, in the present state of European Union law, that by taking the view that those various categories of biomass are not in the same situation the Member States manifestly exceeded the limits of their broad discretion in the matter (see, by analogy, Luxembourg v Parliament and Council, paragraphs 50 and 51). ‘(at 80-81)
This last para is a textbook application of the principle of non-discrimination: treating different situations like, may also constitute a violation of the principle of equal treatment. Here, the difference in circumstance is entirely explained by the ECJ by recourse to the environmental qualities of different types of fuel.