Posts Tagged Waste
Must Article 107 TFEU be interpreted as meaning that a system whereby a private, non-profit eco-body, approved by the public authorities, receives contributions from those who place on the market a particular category of product and who enter into a contract with it to that effect, in return for a service consisting in the organisation on their behalf of the treatment of the waste from those products, and redistributes to operators responsible for the sorting and recovery of that waste, subsidies the amount of which is set out in the approval, in the light of environmental and social targets, is to be regarded as State aid within the meaning of that provision?
That is the question as phrased in C‑556/19 Société Eco TLC and on which Pitruzzella AG Opined on 28 May. TLC stands for Textiles, Lignes de maisons, and chaussures (textiles, household linen and shoes). Producers or as the case may be first importers pay a fee to the collective body in lieu of their personal commitments under extended producers responsibility per Waste Framework Directive 2008/98.
The AG of course revisits the definition of ‘State Aid’ under CJEU C-379/98 Preussen Elektra, on which more here and here. Preussen Elektra remains controversial for it would seem to give Member States quite a bit of room for manoeuvre to reach the same result as direct State Aid more or less simply by inserting a private operator who receivs funds directly from private operators however in line with direct State instructions on level and modalities of payment. The AG opines that in the case at issue there is no State Aid however he directs further factual lines of enquiry (ia re the State control over payments by the collective body to recyclers.
Handbook of EU Waste law, 2nd ed. 2015 OUP, para 4.116 ff.
Your regular waste law teaser. Upper Tribunal finds in Devon Waste Management that ‘Fluff’ is not being discarded.
In  UKUT 0001 (TCC) Devon Waste Management, Biffa and Veolia v Inland Revenue, the tax and chancery chamber of the Upper Tribunal discussed the classification of ‘fluff’ as waste. The fluff at issue is not the type one may find in one’s pockets (or, dare I say, belly button). Rather, the “black bag” waste material that is disposed of at landfill sites and used by operators as a geomembrane liner and geotextile protection layer.
As Constantine Christofi at RPC reports, (see also UKUT at 22) the first tier tribunal – FTT had earlier found that that the use made of the material disposed of was only an indicator of whether there was an intention to discard the material, and that use was not conclusive in determining whether it was discarded. In the view of the FTT, the use of such material as a protective layer was not sufficient to negate an intention to discard it as it was destined for landfill in any event and because there was no physical difference between that material and the other general waste disposed of at the landfill sites. The FTT therefore held that the disposal of the waste was a taxable disposal by way of landfill: not everything that could be characterised as “use” was sufficient to negate an intention to discard.
The FTT had (UKUT does not at all) considered EU law precedent. UKUT relied on English authority and overturned the FTT’s finding on the basis of the FTT having fallen into the “once waste, always waste” trap (at 74). In deciding like this, UKUT itself in my view may have fallen into the alternative ‘once someone’s waste not that of another’ trap. At 52: ‘An owner of material does not discard it, within the meaning of the statutory provisions, if he keeps and uses it for his own purposes’. Making use of materials for the site operator’s purposes connected with regulatory compliance, when they are deposited in the cell, is use that is necessarily inconsistent with an intention to discard the materials.
This arguably is the kind of single criterion test which when it comes to (EU and UK) waste law has been rejected.
In C-654/18 Interseroh Sharpston AG opined on 30 January, in answer to a German court wishing to ascertain whether a waste stream composed principally of paper products should be categorised as so-called ‘green’ waste and therefore subject to the flexible control procedure provided in the EU’s Waste Shipment Regulation 1013/2016. The referring court also asks whether such waste can still be categorised as ‘green’ if it contains up to 10% impurities.
The Regulation combines rules of purely EU origin, with a sometimes complex combination of OECD and 1989 Basel Convention rules. It generally employs a listing system with corresponding light signals (green and amber, previously also red) with the green list being the most desirable to exporters: these only require compliance with the same rules as ordinary commercial transactions.
Regardless of whether or not wastes are included on the list of wastes subject to the Green Control Procedure (Appendix 3 of the EU Regulation), they may not be subject to the Green control procedure if they are contaminated by other materials to an extent which (a) increases the risks associated with the wastes sufficiently to render them appropriate for submission to the amber control procedure, when taking into account the criteria in Appendix 6 to this Decision, or (b) prevents the recovery of the wastes in an environmentally sound manner’.
In the dispute at issue Interseroh collects used sales packaging (lightweight packaging) from private final consumers throughout Germany which it then consigns to recovery. It ships the prepared waste paper across the border for recycling in a paper factory in Hoogezand (Netherlands). New paper and new paperboard is produced from the waste paper. The Netherlands purchaser, ESKA stipulates that the waste paper must meet the following specifications. It should be composed of at least 90% used, residue-drained, system-compatible paper, paperboard or cardboard (PPC) articles and PPC-based combinations, with the exception of liquid packaging board including packaging parts such as labels etc. Also, the waste stream must contain no more than 10% impurities (‘the mixture of wastes at issue’).
The Dutch and German import cq export authorities differ as to the inclusion or not of the transported wastes at issue, with the Dutch taking a more relaxed approach on the basis of the Dutch version of the relevant Basel entry B3020.
- The Dutch version reads „De volgende materialen, mits deze niet vermengd zijn met gevaarlijke afvalstoffen:
Oud papier en karton:
– ongebleekt papier en karton of gegolfd papier en golfkarton; – overig papier en karton, hoofdzakelijk gemaakt van gebleekt chemisch pulp, dat niet in bulk is gekleurd; – papier en karton hoofdzakelijk gemaakt van mechanisch pulp (bv. kranten, tijdschriften en soortgelijk drukwerk); – overige, met inbegrip van: 1. gelamineerd karton, 2. ongesorteerd afval
- The German version: “Folgende Stoffe, sofern sie nicht mit gefährlichen Abfällen vermischt sind:
Abfälle und Ausschuss von Papier und Pappe
– ungebleichtes Papier und Wellpapier und ungebleichte Pappe und Wellpappe; – hauptsächlich aus gebleichter, nicht in der Masse gefärbter Holzcellulose bestehendes anderes Papier und daraus bestehende andere Pappe; – hauptsächlich aus mechanischen Halbstoffen bestehendes Papier und daraus bestehende Pappe (beispielsweise Zeitungen, Zeitschriften und ähnliche Drucksachen); – andere, einschließlich, aber nicht begrenzt auf: 1. geklebte/laminierte Pappe (Karton) , 2. nicht sortierter Ausschuss.
- The English version: The following materials, provided they are not mixed with hazardous wastes:
Waste and scrap of paper or paperboard of:
– unbleached paper or paperboard or of corrugated paper or paperboard; – other paper or paperboard, made mainly of bleached chemical pulp, not coloured in the mass; – paper or paperboard made mainly of mechanical pulp (for example, newspapers, journals and similar printed matter); – other, including but not limited to: (1) laminated paperboard, (2) unsorted scrap.
According to the wording of the German-language version, point 2 of the fourth indent covers ‘nicht sortierten Ausschuss’ (‘unsorted scrap’) and not ‘nicht sortierte Abfälle’ (‘unsorted waste’), as the Dutch Supreme Court held on the basis of the Dutch language version (‘ongesorteerd afval’). The term ‘scrap’ is not synonymous with the terms ‘waste’ or ‘mixture’. In addition, a distinction is drawn in the French language version between ‘mélange de déchets’ and ‘rebuts non triés’, just as in the English-language version between ‘mixture of wastes’ and ‘unsorted scrap’. The terms ‘scrap’ and ‘waste’ are therefore not synonymous. Since, in the Dutch language version of the heading of Basel Code B3020, the term ‘waste’ is not used, but it instead reads ‘papier, karton en papierproducten’, the term ‘afval’ in point 2 of the fourth indent in the Dutch-language version does not cover the entire entry, but only what does not come under the first three indents.
Specifically, on 20 May 2015, the Raad van State (Council of State, Netherlands) ruled in proceedings involving ESKA that a waste paper mixture, regardless of the presence of impurities, comes under Basel Code B3020. Accordingly, any such mixture of wastes constituted ‘Green’ listed waste and came within the list of wastes subject to the Green control procedure under Article 18 of Regulation No 1013/2006. It did so on the basis of the Dutch language version of Basel Code B3020. ESKA had previously been employing the stricter prior notification procedure under Article 4 of the Regulation.
Interseroh then brought an action before the referring German court seeking a declaration that it is entitled to ship the mixture of wastes at issue to other EU Member States in accordance with the Green control procedure.
Sharpston AG at 27 starts by pointing out that the shipments at issue are kosher commercial and regulatory transactions: at least 90% of the mixture is made up of what can be described generically as paper, paperboard and paper product wastes. The waste also includes a maximum of 10% impurities. This, in other words, is not a cowboyesque trafficking practice. She then explores the legislative history of the amended Annexes, paying less attention to the linguistic analysis perhaps than one might expect – object and purpose is, after all, a guiding principle in the interpretation of texts with seemingly diverging language versions. She concludes from that assessment (please refer to her Opinion itself; there is little point in me paraphrasing it here) that the lighter, green list procedure can only apply if the notifier shows with scientific evidence that the level of impurities does not prevent the recovery of the wastes in question in an environmentally sound manner. She also acknowledges at 72 (as the EC already did in its 2009 FAQs) that clarity on the issue is wanting: ‘establishing what is a tolerable level of contamination is a matter that is due (perhaps, overdue) for examination’. However given the lack of formal regulatory guidance on the issue, the Article 28 procedure of Regulation applies: where the competent authorities of the Member State of dispatch and the Member State of destination cannot agree on the classification of a particular consignment of wastes (and hence on whether the more flexible Green control procedure in Article 18 may be used), the Annex IV amber list procedure must be applied.
(Handbook of) EU Waste Law, 2nd ed 2015, Chapter 4.
Kokott AG puts the onus on landfill sites’ operators in dealing with aftercare costs /legacy issues.
In C-15/19 A.m.a. – Azienda Municipale Ambiente SpA v Consorzio Laziale Rifiuti, Kokott AG opined mid-January. Her opinion relies heavily on the specific provisions which the Landfill Directive 1999/31 includes for what one could effectively call legacy issues in waste management: how does one roll-out stricter requirements, including with respect to polluter pays, unto landfill sites that were already in existence?
I shall not repeat said provisions for the Advocate General does so extensively. Suffice to say that her reasoned roll-out of the polluter pays principle (she puts the onus on the landfill sites’ operators; principles of legal certainty do not allow to charge those having deposited the waste at the site retroactively to pay for longer aftercare) is based to a large degree on the window which the Directive foresaw for Member States to close down sites whom they did not think could be expected to meet the new Directive’s stricter obligations before its lenghthy implementation periods; and on the fact that the operators of these sites, unlike the depositors of waste, can be expected to be properly au fait with its aftercare requirements and hence also of the proper amount of charges to be invoiced to users of the site.
Another good example of EU environmental /waste law not quite being the environmental zealot which its critics often try to make of it.
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.
Update 3 July 2020. The conviction was upheld in  EWCA Crim 827.
 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.