Tag: Waste shipments

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Regione Veneto v Plan Eco. CJEU restricts waste classification shopping for mixed municipal wastes.

Judgment in Case C-315/20 Regione Veneto v Plan Eco Srl Is a classic case discussing the scope for Member States to restrict transboundary movements of waste under the Waste Shipments Regulation 1013/2006 (‘WSR). As summarised (2) by Advocate General Rantos, it raises the question whether the classification, in one Member State, of mixed municipal waste in accordance with the European Waste Catalogue (EWC), following mechanical treatment which has not substantially altered the original properties of that waste, interferes with the application of the EU legislation on the shipment of that waste to another Member State.

Transport company Plan Eco submitted to the Veneto Region a request for prior consent to the shipment of 2000 tonnes of mixed municipal waste produced in Italy by Futura Srl to a cement factory in Slovenia (cement kilns are a classic destination for waste for combustion). That waste, of which parties agreed it was not hazardous, was treated mechanically by Futura, with a view to its use in co-combustion, and classified by Futura, after that treatment, under code 19 12 12 (Bottom ash and slag (incinerator bottom ash)) of the EWC. The Veneto Region suggested the waste was mixed municipal waste (code 20 03 01 EWC) and objected to shipment on the grounds that national waste management plans prescribe that mixed municipal waste be recovered in one of the nearest appropriate installations to the place of its production or collection. A Veneto Region facility had  signalled it had capacity to deal with the waste. A classic scenario therefore of a region wanting to keep the waste within its borders so as to satisfy the waste need for local installations.

The Waste Shipments Regulation had, controversially, inserted Article 3(5) which provides that shipments of ‘mixed municipal waste (waste entry 20 03 01) collected from private households, including where such collection also covers such waste from other producers, to recovery or disposal facilities’ are, in accordance with that regulation, subject to the same provisions (Article 11’s principles of self-sufficiency and proximity in particular) as shipments of waste destined for disposal: that means, it gives national and regional authorities more room for manoeuvre to refuse shipments than they would have for waste destined for recovery operations. The Court had earlier (Case C-292/12 Ragn-Sells) confirmed that applicability of Article 11 WSR in principle, without properly addressing the free movement of goods and free movement of services implications.

[27] the Court turns, frustratingly (for in my view binding statutory law should be included in the provisions proper of secondary law, not in their recitals) to Recital 33 of the Waste Framework Directive 2008/98, to hold that mixed municipal waste as referred to in Article 3(5) WSR remains mixed municipal waste even when it has been subject to a waste treatment operation that has not substantially altered its properties. Veneto’s room for refusal therefore widens.

The judgment in this case takes on a new meaning within the context of Brexit, for quite a few of these waste streams have the United Kingdom as their ultimate destination, hence enjoying principled free movement of goods under WTO and UK-EU Trade and Co-operation Agreement rules.

Geert.

 

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A language Fest: Sharpston AG on the Basel Convention and mixtures of wastes in Interseroh.

Update 6 July 2020 The Court held at the end of May (at the time of writing, an EN version is still not available). Given the mixed messages in the language versions of the Regulation’s Annexes, it gives priority to the international agreement which the Regulation is meant to transpose, ie the Basel Convention. From the statutory build-up of the relevant Basel Annex, it holds that mixtures of wastes cannot be classified under one of the relevant entries of the green list; and also that up to 10% impurities do not impact the classification.

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.

Geert.

(Handbook of) EU Waste Law, 2nd ed 2015, Chapter 4.

 

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Ship-generated waste finally at the CJEU: Saugmandsgaard ØE in MSC Flaminia

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?

Geert.

Handbook of EU Waste Law, 2nd ed. 2015, Oxford, OUP, Chapter 3, 3.27 ff.

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TPS-NOLO (Geobal): CJEU on take-back of ‘waste’, relation with REACH.

As I discussed with Stephen Gardner in Bloomberg Environment, the CJEU held yesterday in C-399/17 EC v Czech Republic, where the question is whether the Czech Republic has infringed the waste shipments Regulation 1013/2006 by refusing to take back a substance known as TPS-NOLO (or Geobal) that had been shipped to Poland without respecting the requisite formalities of the Waste Shipment Regulation.

Approximately 20 000 tonnes of TPS-NOLO (Geobal) and composed of tar acid, a remnant after refining oil (code 05 01 07* of the European waste catalogue), of carbon dust and of calcium oxide. Poland considered the substance to be hazardous waste classified in Annex IV to the Waste Shipment Regulation (‘Waste tarry residues (excluding asphalt cements) arising from refining, distillation and any pyrolitic treatment of organic materials’).  The Czech citizen responsible for the shipment to Poland presented the standards adopted by the company as well as proof that the substance in question was registered under the REACH Regulation and that it was used as fuel.

Wahl AG had suggested inadmissability, as I discuss here. The Court however disagreed, and on substance dismissed the EC action in five steps summarised very well in its case-summary. Of note in particular with respect to the REACH /WFD relation is that the Court holds that while the EC is right in being sceptical about WFD evasion via REACH (not that straightforward an assumption, given the cumbersome implications of REACH compliance), the Commission needs to bring specific evidence to the table rather than mere speculation.

Not an earth-shattering case yet a relevant one also with a view to circular economy debates, where REACH’ data requirements are an important concern for recyclers.

Geert.

Handbook of EU Waste law, 2nd ed. 2015, OUP, i.a.at para 1.201.

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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).

Geert.

 

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Wahl AG proposes inadmissability in TPS-NOLO (Geobal): Take-back of ‘waste’, relation with REACH.

Another interesting waste-case at the CJEU last week, although unfortunately one in which Wahl AG proposes inadmissibility. In C-399/17 EC v Czech Republic, the question is whether the Czech Republic has infringed the waste shipments Regulation 1013/2006 by refusing to take back a substance known as TPS-NOLO (or Geobal) that had been shipped to Poland without respecting the requisite formalities of the Waste Shipment Regulation.

Approximately 20 000 tonnes of TPS-NOLO (Geobal) and composed of tar acid, a remnant after refining oil (code 05 01 07* of the European waste catalogue), of carbon dust and of calcium oxide. Poland considered the substance to be hazardous waste classified in Annex IV to the Waste Shipment Regulation (‘Waste tarry residues (excluding asphalt cements) arising from refining, distillation and any pyrolitic treatment of organic materials’).  The Czech citizen responsible for the shipment to Poland presented the standards adopted by the company as well as proof that the substance in question was registered under the REACH Regulation and that it was used as fuel.

The case raises interesting issues therefore on the relationship between REACH and Waste, on which I have written briefly inter alia here and, more extensively and with Dr Thomas de Romph, here. At 3 already, Wahl signals that his Opinion will not however lead to findings on the merits of the case: ‘ Finding that there was no infringement in the present case could potentially weaken the effectiveness and enforceability of the Waste Shipment Regulation, whose main and predominant object and component is protection of the environment. However, courts are guided, first and foremost, by procedural principles that ensure a due process in each individual case. Those principles cannot be sacrificed in order to further a greater cause, as noble as it might be.’

The due process issues essentially relate to the European Commission’s handling of the infringement procedure, in which, the AG suggests proprio motu,  it did not formulate a proper statement of claim. Details are in the Opinion and readers are best referred to it.

Now, there is no such thing as double jeopardy when it comes to infringement proceedings hence one can only hope that the Commission services will reinitiate the proceedings (lest of course the CJEU disagree with the AG’s Opinion).

Geert.

Handbook of EU Waste law, 2nd ed. 2015, OUP, i.a.at para 1.201.

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Seatrade: Ships as waste.

Update 3 December 2019 for a good overview of compliance and banking issues surrounding the case, see here.

Rechtbank Rotterdam held on 15 March last that 4 ships owned and operated by the Sea Trade concern had to be regarded as waste when they left the port at Rotterdam cq Hamburg (they were eventually beached in a variety of destinations). Not having been notified as waste, their shipment was considered illegal and the concern as well as some of its employees consequently convicted. (Illegal waste shipments being a criminal offense).

The court decided not to refer to the CJEU on the application of the waste definition to ships, as it considered the issue to be acte clair. The court’s review of the legal framework is included in Heading 4.3.4. As such, the analysis does not teach us much about the difficulty of applying the waste definition to international maritime logistics, in particular ship disposal. The court found at a factual level that the owners’ intention to dispose of the ships was clearly established when the ships left the EU, with, it suggested, the facts proving that the intention to dispose was at that moment of such an intensity as to trigger the waste definition.

The court does flag its appreciation for the difficulties. Not only is eventual disposal of hardware such as ships a possibility from the moment of their purchase. Such intention may also be withdrawn, reinstated, modified, at various moments of the ships’ life, fluctuating with market circumstances. Particularly given the criminal nature of the legal discipline here, I find that a very important driver to tread very cautiously and to look for firmer objective factors to establish intent.

Most probably to be continued on appeal.

Geert.

(Handbook of ) EU Waste law, 2nd ed. 2017, para 1.20 ff. Disclosure: I acted as court expert.

 

 

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Belgian Council of State highlights authorities’ duty of care in assessing BAT (Export of waste).

The Belgian Council of State (the highest administrative court) has annulled the Flemish waste agency’s export permit in the so-called ‘Slufter’ case, involving large quantities of toxic dredging spoil (for the aficionados: classified as EURAL 17 05 05*; ia with heavy doses of tributyltin – TBT) dredged from the port of Antwerp. The case made by applicants was that the waste would be disposed of in the port of Rotterdam’s ‘slufter’ by way of mere dumping, as opposed to processing ‘at home’ in the Flemish region.

At issue was Article 11 of the Waste shipments Regulation 1013/2006, which allows Member States of export to object to planned shipments of waste destined for disposal. Applicants’ case was that the Flemish waste agency – OVAM should have disallowed the shipment on the basis of the proximity and the self-sufficiency principles. OVAM however pointed out that even if in optimal circumstances, processing in Flanders could lead to higher rates of recovery of the waste, much of it would still simply have to be landfilled. Importantly, it preferred disposal in the Slufter on the basis that the logistics chain was much shorter: load up, transport, dump. As opposed to load up, transport to processing facility for partial recovery (involving three separate processes); load-up of the solid waste left; transport and dump.

The Council of State ruled at the end of May that this decision by OVAM, in particular the reliance of the extent of the logistics chain, lacks proper assessment of the Best Available Technologies for dredging spoil, hence leading to insufficient assessment of the proximity and self-sufficiency principles. The ruling is relevant also with a view to the remainder of the spoil that will continue to be dredged.

For easy of reference (for those wishing to locate copy of the ruling): case numbers are 238220 -238224 included).

Geert.

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Ragn-Sells: Court leaves open violation of primary EU law by waste shipments Regulation – Free movement of services question left unanswered

The ECJ’s December judgment in Ragn-Sells Case C-292/12 came recently to my attention in revisiting the waste ownership and freedom to provide services question for a brief.  The case concerns the combined application of the waste framework Directive, the waste shipments Regulation, the public procurement Directives, the free movement of goods and of services, and, for good measure, competition law, exclusive rights and abuse of dominant position.

The dispute in the main proceedings concerns the lawfulness of contract documents stipulating that mixed municipal waste had to be transported to the landfill facility which was the subject-matter of an earlier public procurement procedure — located 5 km from the contracting town, whilst industrial and building waste was to be taken to a landfill site, located 25 km away.

Not all of these issues were addressed by the ECJ, though: for the issue relating to competition law /creation of exclusive rights which might lead to abuse of dominant position, not enough information had been furnished by the national court.For the issue of free movement of services, there was nothing in the file submitted to the Court indicating that undertakings established in other Member States have been interested in treating waste produced in the territory of the municipality at issue.

The latter especially is a pity (on the competition issue there is plenty of case-law): for the extent of free movement of services in the waste sector (and environmental services generally), is not at all clearly laid out in case-law. Hint for those wanting to use free movement of services arguments in their struggle against restrictive national measures: ensure paper trail of, or indeed if need be, trigger, foreign interest in the waste streams provided.

The Court did entertain the free movement of goods questions. As regards, first of all, waste destined for disposal operations and mixed municipal waste, it follows, the Court held, from Article 11(1)(a) of Regulation No 1013/2006, read in the light of recital 20 in the preamble thereto, and Article 16 of Directive 2008/98, that the Member States may adopt measures of general application restricting shipments of that waste between Member States, in the form of general or partial prohibitions of shipments, by way of implementation of the principles of proximity, priority for recovery and self-sufficiency under Directive 2008/98. By analogy the court then applied Case C‑209/98 Sydhavnens to find eventually that ‘Accordingly, in the case of waste destined for disposal operations and mixed municipal waste collected from private households and, as applicable, other producers, a Member State may confer on local authorities, on the geographical scale it deems appropriate, powers to manage the waste produced on their territory in order to ensure compliance with its obligations under Article 16 of Directive 2008/98. Those authorities may, as part of the powers conferred upon them, provide that those types of waste will be treated in the nearest appropriate facility (at 63).

I continue to argue that especially with respect to mixed municipal waste, this room for manoeuvre provided for by the Regulation combined with the Directive, itself is incompatible with primary EU law. However I am not sure how much longer I can argue that as a result of judicial economy, the ECJ has never really properly addressed this question.

As regards, secondly, shipments of waste destined for recovery operations, other than mixed municipal waste, the Court by contrast held that the combined effect of Regulation and Waste Framework Directive does not provide for the possibility for a national authority to adopt a measure of general application having the effect of prohibiting, totally or partially, shipments of such waste to other Member States for treatment.

In summary, some remaining doubt re free movement of goods (primacy EU law) in my mind. Undoubtedly a lot of remaining doubt re free movement of services. Waste law and free movement: they continue to fascinate!

Geert.

 

 

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RERA: a weee chance of US Basel ratification?

Many thanks to Gideon Kracov for pointing this out to me: the proposed Responsible Electronics Recycling Act (a private member’s Bill) would install an EU-type regime on the export of electric and electronic waste outside of the US. The US have signed but not  ratified the Basel Convention : RERA would amount to implementation of the Convention in practice. The Bill also recognises the relevance of recovering the many rare earth materials contained in WEEE.

Here’s the blurb (the official summary of the Bill, in fact):

_______________

Introduced in House (07/23/2013)

Responsible Electronics Recycling Act – Amends the Solid Waste Disposal Act to: (1) prohibit the export of restricted electronic waste to countries that are not members of the Organization for Economic Cooperation and Development (OECD) or the European Union (EU), or Liechtenstein; (2) require the Administrator of the Environmental Protection Agency (EPA) to develop and promulgate procedures for identifying certain electronic equipment as well as additional restricted toxic materials contained in such equipment which poses a potential hazard to human health or the environment; and (3) establish criminal penalties for knowingly exporting restricted electronic waste in violation of this Act. Allows certain exceptions to such export ban.

Defines “restricted electronic waste” to include electronic equipment (excluding parts of a motor vehicle), such as computers, televisions, printers, copiers, video game systems, telephones, and similar used electronic products, that contain cathode ray tubes, batteries, switches, and other parts containing lead, cadmium, mercury, organic solvents, hexavalent chromium, beryllium, or other toxic ingredients.

Requires persons who handle restricted electronic wastes to permit appropriate EPA and state officials access to such wastes upon request.

Directs the Secretary of Energy to establish a competitive research application program to provide grants for research in the recovering and recycling of critical minerals and rare earth elements found in electronic devices.

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