Posts Tagged Waste
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.
Arica Victims v Boliden Mineral (Sweden). Lex causae and export of toxic waste. Relevant for the business and human rights /CSR debate.
I reported earlier on the decision at first instance in Arica Victims v Boliden Mineral. The Court of Appeal has now reversed the finding of Chilean law as lex causae, opting instead for Swedish law. Lindahl has good review here and I rely on it quite heavily for I do no speak Swedish.
Boliden Mineral exported toxic waste to Chile in the ’80s, prior to either Basel or EU or OECD restraints (or indeed bans) kicking in. A first issue for consideration was determination of lex causae. Rome II does not apply ratione temporis (it only applies to tortious events occurring after its date of entry into force) – residual Swedish private international law applies. My understanding at first instance was that the applicable law rule referred to lex loci damni, Chile. The Court of Appeal has gone for lex loci delicti commissi: whether this was by use of an exception or whether the court at first instance had simply misunderstood Swedish PIL, I do not know.
Having opted for lex loci delicti commissi, the Court of Appeal then considered where this was. Readers of the blog will know that this is relevant for CSR /business and human /environmental rights discussions. Lindahl’s Linda Hallberg and Tor Pöpke summarise the court’s approach:
In order to determine which country’s law applied to the case, the court examined a sequence of events that had influenced, to varying degrees, what had led to the alleged damage. According to the court, the decisive factor in the choice of law were acts and omissions that could be attributed to the Swedish mining company, as the case concerned this company’s liability for damages.
Instead of determining the principal location of the causative events using quantitative criteria, the court considered it to be where the qualitatively important elements had their centre of gravity. Further, in contrast with the district court’s conclusion, it held that the Swedish mining company’s alleged negligence had its centre in Sweden and therefore Swedish tort law should be applied in this case (the law of the place in which a delict is committed).
Unlike more ‘modern’ CSR cases the fact do not concern mother /daughter company relations yet the considerations of locus delicti commissi are nonetheless interesting.
The Court of first instance had employed Chilean’s longer statute of limitation. The Court of Appeal tried to stretch Sweden’s shorter one of 10 years (the case concerns a potentially tortious act which occurred more than 30 years ago): any subsequent damage that had been caused by the mining company’s failure to act during the period after the toxic waste had been shipped to Chile would advance the starting point for the limitation period. However this was at the latest 1999 and the 2013 action therefore had been taken too late.
On 25 June last the Supreme Court rejected further consideration, the Court of Appeal’s finding therefore stands.
(Handbook of) EU Private International Law, 2nd ed. 2016, Chapter 4, Heading 4.6.3, Chapter 8.
d EWCA Crim 20 Regina v BIFFA Waste Services is a rare example of interlocutory appeal concerning jury instruction and summing up. It involves Regulation 1013/2006, the Waste shipments Regulation, particularly the EU’s enforcement of the ‘Basel Ban‘: the ban on exports of hazardous wastes destined for disposal in non-OECD countries.
The only real point arising on appeal is whether (contrary to the judge’s approach at Crown Court) the prosecution was to be required to show not just that a shipment of wastes was not ‘Green List’ wastes but rather household (domestic) wastes, but in addition, to prove that the waste was contaminated by other materials to an extent which prevented the recovery of waste in an ‘environmentally sound manner’ (the general Basel condition for exports); and whether the jury was to be instructed in the summing-up accordingly.
The containers in question were to form part of a larger consignment of containers (448 in total) destined for China. In May and early June 2015 they were the subject of interception and examination at the port of Felixstowe by officials of the Environment Agency. It is asserted that such examination revealed that these particular containers, or some of them, included significant contamination by items which were not mixed paper items at all; for example, soiled nappies and sanitary wear, sealed bags of excrement, clothing, food packaging, plastic bottles and so on. It is asserted that this was indicative of the consignments being mixed household waste rather than mixed paper waste: it being common ground that household waste, as such, could not be lawfully exported in this way to China.
Of particular specific relevance for the appeal is Recital (28) of the Waste Shipments Regulation which provides “It is also necessary, in order to protect the environment of the countries concerned, to clarify the scope of the prohibition of exports of hazardous waste destined for recovery in a country to which the OECD Decision does not apply, also laid down in accordance with the Basel Convention. In particular, it is necessary to clarify the list of waste to which that prohibition applies and to ensure that it also includes waste listed in Annex II to the Basel Convention, namely waste collected from households and residues from the incineration of household waste.”
Davis LJ at 33 deals swiftly with the issue. Appreciating that plenty could be said about the precise application of the Regulation, he nevertheless simply points to the prosecution’s intention. They have never sought to say that these were consignments which were indeed essentially Heading B3020 waste paper but nevertheless contaminated by other materials not collected from households (for example, corrosive fluids or dangerous metals etc). so as to prevent recovery of the waste in an environmentally safe manner. They had relied solely on showing the jury that the shipment was not paper waste. If it was, then the waste in question could not be B3020 waste paper (which is within the “green” list of waste which may legitimately be exported). If it was proved that the relevant consignments were indeed heading Y46 waste (household waste) instead, then that was within Article 36(1)(b) of the Regulation and that was the end of the matter. If, on the other hand, the prosecution failed to prove that the relevant consignments were indeed Y46, then that too was the end of the matter and the defendant was entitled to be acquitted.
At 36 he ends with congratulatory remarks to judge Auerbach at Crown Court:
In a matter which is by no means the common currency of Crown Courts, he speedily produced a comprehensive reserved written ruling which set out in full detail the legislative background and authorities; fully analysed and discussed the competing arguments; and explained the reasons for his conclusion with crystal clarity. It is just because of the care and detail underpinning his ruling that this court has been able to approach matters rather more succinctly than otherwise might have been the case.’
(Handbook of) EU Waste Law, 2nd ed 2015, Chapter 4.
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.
(Handbook of) EU Waste law, 2nd ed. 2015, Oxford, OUP, Chapter 1, 1.149 ff.
Update 25 June 2019 for good, more detailed review see Reed Smith here.
Update 22 May 2019 on 16 May the CJEU confirmed the literal reading of the AG.
I fear I do not have the time or opportunity for the moment fully to analyse Saugmandsgaard ØE’s Opinion at the end of January in C-689/17 MSC Flaminia (no EN version available) – hence this post is a flag more than a review. The second Opinion of the AG in the same month (see C-634/16 ReFood) on the waste shipments Regulation.
Readers beware: there are two distinct exemptions for ships-related waste in the waste shipments Regulation: are exempt:
the offloading to shore of waste, including waste water and residues, generated by the normal operation of ships and offshore platforms, provided that such waste is subject to the requirements of the International Convention for the Prevention of Pollution from Ships, 1973, as modified by the Protocol of 1978 relating thereto (Marpol 73/78), or other binding international instruments; and
waste generated on board vehicles, trains, aeroplanes and ships, until such waste is offloaded in order to be recovered or disposed of.
In the case at issue: does the latter cover residues from damage to a ship at sea in the form of scrap metal and fire extinguishing water mixed with sludge and cargo residues on board the ship?
Handbook of EU Waste Law, 2nd ed. 2015, Oxford, OUP, Chapter 3, 3.27 ff.
The Court held today in C-60/18 AS Tallinna Vesi and agrees with its AG re the possibility of national criteria, yet unlike Ms Kokott does not see an obligation in the WFD for the Member States to have a proactive vetting and decision procedure. It does not give much specification to its reasoning, other than a reference to the ‘circumstances of the case’. This may refer, but I am speculating, to applicant wanting the authorities generally to sign off on its production method, rather than requesting an opinion on an individual stream. In other words: fishing expeditions must not be entertained.
If my interpretation is right it underscores what I have remarked elsewhere on the regulatory process, for instance in the case of circular economy: in a grey regulatory zone, we need to think of mechanisms to assist industry in embracing environmentally proactive solutions, rather than driving them into incumbent technologies or worse, illegality. The CJEU’s view is in line with Williams J in Protreat – however I do not think it is the right regulatory path as I also suggest (in Dutch) here.
Handbook of EU Waste law, 2nd ed. 2015, OUP, 1.166 ff and 1.189 ff.
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.
(Handbook of) EU Waste law, 2nd ed. 2015, Oxford, OUP, Chapter 1, 1.149 ff.