Tag: circular economy

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Sappi Austria: CJEU tries to keep a common sense approach to supporting the circular economy and maintaining the objectives of EU waste law.

Case C‑629/19 Sappi Austria Produktions-GmbH & Co. KG and Wasserverband ‘Region Gratkorn-Gratwein’ v Landeshauptmann von Steiermark in which the CJEU held on Wednesday is in my off the cuff view (I did not research it in the recent case-law) the first case where the CJEU specifically mentions the objectives of the circular economy to support its interpretation of the core definition of ‘waste’ in the Waste Framework Directive 2008/98.

Sappi operate a large industrial paper and pulp production plant in Gratkorn (Austria). On that site is also a sewage treatment plant, operated jointly by Sappi and the Wasserverband, which treats waste water from paper and pulp production as well as municipal waste water. During the treatment of that waste water, which is required by national law, the sewage sludge in question in the main proceedings arises. That sludge is therefore made up of both substances from industrial waste water and substances from municipal waste water. Sewage sludge which is produced in the sewage treatment plant is then incinerated in a boiler of Sappi and in a waste incineration plant operated by the Wasserverband, and the steam reclaimed for the purposes of energy recovery is used in the production of paper and pulp.  hat authority found that, admittedly, the majority of the sewage sludge used for incineration, namely 97%, originated from a paper production process and that this proportion could be regarded as having ‘by-product’ status within the meaning of Paragraph 2(3a) of the AWG 2002. However, that does not apply to the proportion of sewage sludge arising from municipal waste water treatment. That sewage sludge remains waste. Since there is no de minimis limit for the classification of a substance as ‘waste’, the authority assumed that all the sewage sludge incinerated in the industrial plants of Sappi and of the Wasserverband must be classified as ‘waste’.

The CJEU first of all holds that there is no relevant secondary law which provides the kinds of qualitative criteria for sewage sludge to meet with the objectives of the WFD. If there were such laws, and the sludge meets their requirements, it would be exempt form the WFD. It then reminds the referring court, of course, of the extensive authority on the notion of waste (most recently C-624/17 Tronex) yet is happy to provide the national Court with input into the application in casu.

In principle, the sludge is waste, the Court holds: it is a residue from waste water treatment and it is being discarded.

However, the referring judge suggests that the sludge may meet the requirements of A6(1) WFD as being fully ‘recovered’ before it is used in the incineration process. It is there that the CJEU refers to the circular economy: at 68:

it is particularly relevant that the heat generated during the incineration of the sewage sludge is re-used in a paper and pulp production process and that such a process provides a significant benefit to the environment because of the use of recovered material in order to preserve natural resources and to enable the development of a circular economy.

Per C‑60/18 Tallinna Vesi, the recovery of sewage sludge entails certain risks for the environment and human health, particularly linked to the potential presence of hazardous substances. For the sludge at issue here not to be waste, presupposes that the treatment carried out for the purposes of recovery makes it possible to obtain sewage sludge with a high level of protection of the environment and human health, such as required by the WFD, which is, in particular, free from any dangerous substance. For that purpose, it is necessary to ensure that the sewage sludge in question in the main proceedings is harmless (at 66). The CJEU concludes, at 67

It is for the referring court to determine whether the conditions laid down in Article 6(1) of Directive 2008/98 are already met before the sewage sludge is incinerated. It must in particular be determined, as appropriate, on the basis of a scientific and technical analysis, that the sewage sludge meets the statutory limit values for pollutants and that its incineration does not lead to overall adverse environmental or human health impacts.

There are as yet no EU standards for the full recovery of sewage sludge, hence the ball of end of waste status is once again in the Member States’ court.

Geert.

(Handbook of) EU Waste law, 2nd ed. 2015, Oxford, OUP, Chapter 1, 1.149 ff.

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Prato Nevoso Termo Energy. The CJEU on end of waste, precaution and 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.

Geert.

Handbook of EU Waste law, 2nd ed. 2015, OUP, 1.166 ff and 1.189 ff.

 

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Tronex. Determining ‘waste’ in reverse logistics chains. CJEU supports holders’ duty of inspection, rules out consumer return under product guarantee as ‘discarding’.

I reviewed Kokott AG’s Opinion in C-624/17 OM v Tronex here. The Court yesterday essentially confirmed her Opinion – readers may want to have a quick read of my previous posting to get an idea of the issues.

The Court distinguishes between two main categories. First, redundant articles in the product range of the retailer, wholesaler or importer that were still in their unopened original packaging. The Court at 32: ‘it may be considered that those are new products that were presumably in working condition. Such electrical equipment can be considered to be market products amenable to normal trade and which, in principle, do not represent a burden for their holder.’ However (at 33) that does not mean that these can never be considered to be ‘discarded’: the final test of same needs to be done by the national court.

The second category are electrical appliances returned under the product guarantee. At 43: goods that have undergone a return transaction carried out in accordance with a contractual term and in return for the reimbursement of the purchase price cannot be regarded as having been discarded. Where a consumer effects such a return of non-compliant goods with a view to obtaining a reimbursement of them under the guarantee associated with the sale contract of those goods, that consumer cannot be regarded as having wished to carry out a disposal or recovery operation of goods he had been intending to ‘discard’ within the meaning of the Waste Framework Directive. Moreover per C-241/12 and C-242/12 Shell, the risk that the consumer will discard those goods in a way likely to harm the environment is low.

However such a return operation under the product guarantee does not provide certainty that the electrical appliances concerned will be reused. At 35: ‘It will therefore be necessary to verify, for the purposes of determining the risk of the holder discarding them in a way likely to harm the environment, whether the electrical appliances returned under the product guarantee, where they show defects, can still be sold without being repaired to be used for their original purpose and whether it is certain that they will be reused.’

At 36: if there is no certainty that the holder will actually have it repaired, it has to be considered a waste. At 40 ff:  In order to prove that malfunctioning appliances do not constitute waste, it is therefore for the holder of the products in question to demonstrate not only that they can be reused, but that their reuse is certain, and to ensure that the prior inspections or repairs necessary to that end have been done.

The Court ends at 42 with the clear imposition of a triple duty on the holder (who is not a consumer, per above): a duty of inspection,  and, where applicable, a duty of repair and of packaging.

Geert.

(Handbook of) EU Waste law, 2nd ed. 2015, Oxford, OUP, Chapter 1, 1.149 ff.

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Tronex. Circular economy, reverse logistics qualifying as wastes return to the CJEU. Kokott AG suggests a duty of prompt inspection.

Kokott AG Opined in C-624/17 OM v Tronex end of February (I had flagged the case summarily earlier): whether consumer returns of electrical appliances some of which are no longer usable because defective, and residual stock are to be regarded as waste that may be exported only in accordance with the Waste Shipment Regulation. – Reminiscent of the issues in Shell: in that case in a B2B context.

Tronex’ export consignment that was stopped, consisted of appliances which had been returned by consumers under a product guarantee, on the one hand, and goods which, because of a change to the product range, for example, were or could no longer be sold (normally), on the other. A number of the boxes in which the appliances were packaged carried a notice stating their defects. The glass in some of the glass kettles was damaged. The shipment was to take place without notification or consent in accordance with the Waste Shipment Regulation.

The AG takes a sensible approach which distinguishes between consumer and collector. At 31 ff: The mere fact that objects have been collected for the purpose of reuse does not in itself necessarily support the assumption that they have been discarded. Indeed, it seems sensible, both economically and from the point of view of the efficient use of resources, to make appliances which can no longer be sold on the market for which they were originally intended available on other markets where they may still sell. Particularly in the case of residual stock which is still in its unopened original packaging, therefore, the request for a preliminary reference contains insufficient evidence to support the conclusion that there has been any discarding.

Returned appliances which, on account of serious defects, are no longer usable and can no longer be repaired at reasonable cost, on the other hand, must unquestionably be regarded as waste. Kokott AG suggests waste classification as the default position. At 39: in so far as there are doubts as to the reuse of the goods or substance in question being not a mere possibility but a certainty, without the necessity of using any of the waste recovery processes referred to in the Waste Directive prior to reuse, only the possibility of ‘prompt’ dispelling of the doubt by an inspection of the appliances, can shift the presumption of it being waste.

‘Repair’ is what the AG proposes as the distinctive criterion: at 40: if the inspection shows that the item is still capable of functional use, its status as waste is precluded. The same is true of goods with minor defects which limit functionality only negligibly, meaning that these goods can still be sold without repair, in some cases at a reduced price. At 41: ‘In so far as the inspection identifies defects which need to be repaired before the product is capable of functional use, however, that product constitutes waste, since there is no certainty that the retailer will actually carry out the repair. Whether the repair is less or more expensive cannot be decisive in this regard, since a product that does not work constitutes a burden and its intended use is in doubt.’ The same goes for goods (other than those in the original packaging, per above) which have not been inspected at all.

At 45 ff the AG supports this conclusion with reference to instruction in Annexes to the WEEE Directive. She also suggests that her interpretation, given the criminal law implications, be limited to those instances occurring after the eventual CJEU judgment.

Geert.

(Handbook of) EU Waste law, 2nd ed. 2015, Oxford, OUP, Chapter 1, 1.149 ff.

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Time to update the Waste Handbook. The circular economy package published. OJ [2018] L150.

One or two of you are aware I have written a whole handbook on EU waste law. That now needs updating as a result of the publication of the adopted ‘Circular Economy package’ – although implementation dates are some time off so if you do have a copy, do not discard it just yet.

The package includes amendments to the ELV, Batteries, WEEE, Landfill, packaging and packaging waste, and waste framework Directive.

I am hoping to write a paper on the package which will summarise the developments – watch this space.

Geert.

Handbook of EU Waste law, 2nd ed. 2015: all chapters 🙂 .

 

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The circular economy and waste to energy. A concise contemplation.

I am in Wuhan 2 1/2 days this week, where I am pleased to be engaging in three of my favourites: a class on environmental law, at Wuhan University’s unparalleled Research Institute of Environmental Law; a session on best practices for PhD research at same; and a conference presentation on conflict of laws at the solidly A+++ ‘Global Forum’ of the Chinese Society of Private International Law and Wuhan University’s Institute of International Law.

Anyways, on my way I inter alia wrote following intro to a volume on Waste to Energy, edited by Harry Post. I thought would share.

The European Union purports to be moving towards a Circular Economy (CE). If recent experience in environmental and energy law is anything to go by, the rest of the world will look with interest to its progress. It is fashionable to say that in the CE ‘waste’ will no longer exist. This is however not relevant beyond semantics. What really matters is how the EU and others after or before it, create the economic and regulatory environment that enables the innovation which a CE requires.

Regulatory circles have ample sympathy for business implementing and bringing to market the many exciting ideas which engineers continue to develop. At the same time one must not be blind to the excess which unchecked engineering imagination does have on society, in all pillars of sustainable development: social, economic and environmental. We must not compromise on a robust regulatory framework which looks after what public health and environmental protection require: two Late Lessons from Early Warnings reports tell us that we would do so at our own peril. However we do have to question continuously whether our existing laws are best practice in reaching that desired outcome. It would be a particular affront if innovative products and services that truly may boost environmental protection, were not to be rolled-out because of anxiety over their legal status.

In an innovative environment, legal certainty is an important driver for success. Lack of clarity over the legal framework and /or the regulators’ implementation of same, leads industry either to seek out and concentrate development on those States with lax or flexible regulators only; or to stick to old and trusted products.

The European Union is particularly suited to providing that clarity. On the scientific front, by investing in research and development, especially at SME and specialised spin-offs level. On the regulatory front, it would do well to work out a regime which enables innovators to query enforcement agencies about the legality of a new product or service line without the fear of subsequently being disciplined for it.

This volume is a scholarly effort to assist with both strands of the exercise. It is to be much commended for that effort and I for one am sure both industry and legal scholars will find its content encouraging.

Geert.

 

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Sjelle Autogenbrug, CJEU defines second hand goods.

A quick note on second-hand goods and VAT. For my review of Bot AG’s Opinion in C-471/15 Sjelle Autogenbrug, see here. The Court held yesterday and defined (at 32) second-hand goods essentially as follows: in order to be characterised as ‘second-hand goods’, it is only necessary that the used property has maintained the functionalities it possessed when new, and that it may, therefore, be reused as it is or after repair.

The Court does not refer to EU waste law yet the impact on that area of EU law is clear.

Geert.

Handbook of EU Waste Law, second ed. 2016, Chapter 1.

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Sjelle Autogenbrug, second hand goods. A core tutorial on the VAT mechanism and how in law, all is connected.

In C-471/15 Sjelle Autogenbrug, Bot AG opined a few weeks ago. I find myself curiously drawn to VAT cases these days. Especially since I reported how in a VAT case, the CJEU perhaps accidentally came to a major decision on the Aarhus Convention. Also have a look for instance on how the same AG discusses ‘cultural services’ within the context of VAT (C-592/15 BFI). Or perhaps it is because I have a past (and potentially, a future) in customs duties and excise.

It is particularly interesting to ponder how terminology that is used across the board in EU law, specifically also regulatory law, is interpreted in the context of VAT. (Incidentally the Advocate General gives an excellent summary of VAT rules and why VAT can /should be set-off between traders). In the case at hand, Directive 2006/112 provides i.a. the following definition for second-hand goods: “second-hand goods” means movable tangible property that is suitable for further use as it is or after repair, other than works of art, collectors’ items or antiques and other than precious metals or precious stones as defined by the Member States; 

Sjelle Autogenbrug I/S is a vehicle reuse undertaking whose main activity is the resale of used motor vehicle parts which it removes from end-of-life vehicles. It also engages in the environmental and waste treatment of end-of-life vehicles, a service for which it charges a standard price. Lastly, a lesser part of the undertaking’s overall turnover derives from the sale of scrap metal remaining after removal of the motor vehicle parts. Sjelle Autogenbrug purchases end-of-life vehicles — which are either vehicles whose lifespan has expired or total write-offs — from individuals and insurance companies who do not declare VAT on sales made. Sjelle Autogenbrug currently declares VAT pursuant to the applicable general rules. In 2010, it asked the tax authorities to apply the special margin scheme for second-hand goods to its activity of reselling used motor vehicle parts taken from end-of-life vehicles. The authorities refused.

Since the goods are reintroduced into the distribution chain, the taxable dealer is liable for VAT when he resells the goods. However, as the taxable dealer did not pay VAT when he purchased the second-hand goods from the non-taxable individual, he cannot deduct such VAT from the amount to be paid to the State, being an amount comprised exclusively of the VAT charged upon resale of those goods. This results in a lack of VAT neutrality and in the double taxation of the goods (at 26). The margin scheme was adopted to alleviate that difficulty. It aims to harmonise the rules applicable to the acquisition of new goods subject to VAT which are later resold as second-hand goods and to prevent double taxation and the distortion of competition between taxable persons in the area of second-hand goods.

The Danish government submits that the use in that provision of the words ‘as it is’ demonstrates that, in order to be classified as ‘second-hand goods’, the goods must retain their identity, which is not the case with spare parts since Sjelle Autogenbrug acquires, first of all, a complete vehicle. Furthermore, it argues that even if those spare parts could be classified as ‘second-hand goods’, it would not be possible to apply the margin scheme because the purchase price of the spare parts cannot be precisely determined.

Bot AG disagrees:

  • the EU legislature did not intend to exclude goods originating from a single whole which could be separated, such as parts taken from end-of-life vehicles (at 33)
  • the key factor in the classification of goods as ‘second-hand goods’ is that the used goods must retain the characteristics they had when new (at 35). He refers in this context also tho the end-of life-vehicles Directive, 2000/53, which defined ‘reuse’ as ‘any operation by which components of end-of-life vehicles are used for the same purpose for which they were conceived’. ‘Motor vehicle parts fall squarely within that definition since, even when separated from the vehicle, they retain their original characteristics as they will be reused for the same purpose in another vehicle. The fact that those parts were removed from the vehicle is therefore of little consequence.‘ (at 35)

The Advocate General further considered that were the special margin scheme not to be applied, dealers of second hand spare parts would be disfavoured vis-a-vis those dealing in new spare parts. Hardly indeed a result that would be conducive to the circular economy.

EU waste law does not employ the notion ‘second hand goods’. In practice these goods have raised all sorts of demarcation issues. Summarising all these, if one and the same good is simply passed on to ‘a second hand’, ie the original owner no longer has a use for it but it can be passed on by someone else who will employ it for its original purpose and without there being a need for treatment or processing, it should not be regarded as waste.

It is only be looking into all nooks and crannies of EU law that  ambitious projects like the circular economy will be a real success. Current Opinion is a good illustration of such successful consideration.

Handbook of EU Waste Law, second ed. 2016, Chapter 1.

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Proposed EU e-commerce rules further reduce choice for consumer contracts.

I have referred repeatedly in the past to an inevitable attraction which some find in harmonising private, incuding contract law, in the Member States. The Common European Sales Law (CESL) proposal is dead, and for good reason. Its demise however has not led to the European Commission leaving the path of harmonisation in contract law. The EC has now selected bits and pieces of the CESL approach which it reckons might pass Member States objections. The proposed ‘fully harmonised’ rules on e-commerce formally do not close the door on party autonomy in the contracts under their scope of application. Yet in forcing regulatory convergence top-down, the aim is to make choice of law for these contracts effectively nugatory.

The EC itself formulates it as follows (COM(2015)634, p.1:

“This initiative is composed of (i) a proposal on certain aspects concerning contracts for the supply of digital content (COM(2015)634 final), and (ii) a proposal on certain aspects concerning contracts for the online and other distance sales of goods (COM(2015)635 final). These two proposals draw on the experience acquired during the negotiations for a Regulation on a Common European Sales Law. In particular, they no longer follow the approach of an optional regime and a comprehensive set of rules. Instead, the proposals contain a targeted and focused set of fully harmonised rules.”

Consequently the same proposal reads in recital 49 ‘Nothing in this Directive should prejudice the application of the rules of private international law, in particular Regulation (EC) No 593/2008 of the European Parliament and of the Council and Regulation (EC) No 1215/2012 of the European Parliament and the Council‘: that is, respectively, Rome I and Brussels I Recast’.

Consequently and gradually, choice of law for digital B2C contracts becomes redundant, for the content of national law converges. Support for this in my view is not rooted in fact (the EC’s data on the need for regulation have not fundamentally changed since its doomed CESL proposal), neither is it a good development even for the consumer. National consumer law is able to adapt, often precisely to the benefit of the consumer, through national Statute and case-law. Turning the EU regulatory tanker is much more cumbersome. The circular economy, recently often debated, is a case in point. Many national authorities point to limitations in contract law (incuding warranty periods and design requirements) as an obstacle to forcing manufacturers, including for consumer goods, to adopt more sustainable manufacturing and distribution models. The EC’s current proposals do no meet those challenges, rather, they obstruct them.

Geert.

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