Tag: Waste

Posted on

Porr Bau: The CJEU encourages the circular economy and resource efficiency in its approach of waste law and excavated, uncontaminated soil.

The Court yesterday held in C-238/21 Porr Bau. I reviewed Medina AG’s Opinion here.

The Court notes ia [27] Austria’s contention that, under Austrian law, where materials are excavated or demolished in the course of a construction project, the main purpose of the construction developer is usually to carry out that project without being hindered by those materials, with the result that they are removed from the site in question with the intention of discarding them.  That sentence already holds the key to the eventual judgment in the word ‘usually’.

The Court like, as I noted, the AG, repeatedly refers to Sappi Austria. [47] following from the various elements considered in Sappi Austria (which itself cross-refers to eg CJEU Shell), the national court is instructed to determine whether the excavated materials constituted a burden which that construction undertaking sought to discard, with the result that there would be a risk that that undertaking would discard them in a manner likely to cause harm to the environment, particularly by dumping them or disposing of them in an uncontrolled manner. [49]:

In the present case, it is apparent from the information before the Court that, even before the excavation of the materials at issue in the main proceedings, local farmers had made an express request for the supply of such materials. After appropriate construction projects had been found, making the requested excavated materials available, that request, it is stated, led to a commitment by Porr Bau to make those excavated materials available, alongside an agreement under which that undertaking would carry out, by means of those materials, the works to adapt and improve the land and cultivation areas duly identified. Such factors, if proven which it is for the referring court to determine, do not appear to be such as to establish the intention of the construction undertaking concerned to discard those materials.

The Court then leaps to an assessment of whether the soil may be considered a by-product under Article 5 WFD, in a logical sequence which I still do not quite get: [50]

It is, therefore, necessary to examine whether the excavated materials at issue in the main proceedings must be classified as a ‘by-product’ within the meaning of Article 5(1) of Directive 2008/98.

It is the ‘therefore’ which I do not understand. If a party does not ‘discard’ the materials which the Court seems to suggest is the case here, then the ‘waste’ definition is not met. There is then no need to consider whether the materials might be ‘by-products’, for this would mean that if the scenario does not meet with the A5 ‘by-products’ definition, they might nevertheless have to be regarded as waste despite the earlier determination of there not being an element of discarding.

The Court nevertheless assesses all A5 criteria leading it strongly to suggest that these products are indeed by-products. It repeats in my view its fallacy of the waste-by products relationship in the dictum of the judgment:

Point 1 of Article 3 and Article 6(1) of Directive 2008/98/EC of the European Parliament and of the Council of 19 November 2008 on waste and repealing certain Directives,

must be interpreted as precluding national legislation under which uncontaminated excavated materials, which, pursuant to national law, are in the highest quality class,

–      must be classified as ‘waste’ where their holder neither intends nor is required to discard them and those materials meet the conditions laid down in Article 5(1) of that directive for being classified as ‘by-products’, and

–      only lose that waste status when they are used directly as a substitute and their holder has satisfied the formal criteria which are irrelevant for the purposes of environmental protection, if those criteria have the effect of undermining the attainment of the objectives of that directive.

It also rebukes the Austrian regime from the point of view of end of waste status, dismissing some of the Austrian requirements for a material to be able to reach that status, as irrelevant and counter-productive to the objectives of the WFD. These requirements are said to be “formal criteria (in particular record-keeping and documentation obligations) which have no  environmentally relevant influence” however neither the CJEU nor the referring court give any further detail.

This is a first chamber, in a five -judge composition. I don’t think it has definitively solved the relationship between ‘waste’ and ‘by-products’.

Geert.

EU Waste law, 2nd ed 2015, 1.20 ff.

Posted on

Porr Bau. Medina AG on waste and end-of-waste status of excavated soil.

Medina AG’s end June Opinion in C-238/21 Porr Bau GmbH v Bezirkshauptmannschaft Graz-Umgebung will delight waste lawyers for the case once again evolves around the definition of ‘waste’ as applied to excavated soil. Statute to be interpreted is the WFD or the Waste Framework Directive 2008/98. CJEU SAPPI is a recent judgment  often referred to by the AG.

Porr Bau, the applicant in the main proceedings, is a construction undertaking established in Austria. In July 2015, certain local farmers asked it to supply them, against payment, with excavated soil and to distribute it over their properties. The purpose of the farmers’ request was to level their agricultural land and improve their cultivation areas, thereby increasing yields. Porr Bau applied to the relevant authorities for a statement that the soil was not to be considered waste so as it could avoid a number of taxes. That authority disagreed and also held that the soil, which it considered to be waste, had not yet reached end-of-waste status.

The AG (36) opines that it should not be assumed that all excavated soil by a construction undertaking is by default to be discarded, and that it is difficult to conclude that, under circumstances such as those of the present case, the intention of a construction undertaking is to discard excavated soil that has been carefully selected, subjected to a quality control and supplied as uncontaminated top-quality material in order to attend to a specific request from local operators in need of that material. He also suggests, less convincingly in my view, (38 ff) that such soil may be considered a by-product of the construction sector. 

Should he not be followed on the waste definition issue, the AG suggests and he is right in my view that national law must not deny end-of-waste status until the holder fulfils certain formal requirements with no environmental relevance such as record-keeping and documentation obligations.

Geert.

EU Waste law, 2nd ed 2015, 1.20 ff.

Posted on

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.

 

Posted on

The Antwerp court of first instance in CMB (Bocimar NV), ‘The Mineral Water’: In dubio pro reo or a perfect excuse for forum shopping?

The Antwerp court of first instance (criminal section) has held last Friday, 25 June (I have copy of the judgment (in Dutch) on file) in the prosecution against CMB (an Antwerp based shipowner; specifically: Bocimar NV) and a number of individuals for the alleged illegal transport of waste, in the shape of the discarded ship the Mineral Water, destined for beaching at Chittagong, Bangladesh (the same location of relevance in Begum v Maran).

The Mineral Water was built in 1999, bought by CMB in 2007. A decision was made ‘end 2015’ (the judgment does not clarify specific date and /or circumstance of that decision) to sell  her, with a view to recycling. That sale was approved on 19 January 2016 by Bocimar Board Decision, to a cash buyer based on the British Virgin Islands, when the ship was anchored at Fangcheng, China. Actual transfer of the ship happened at Malaysia a few weeks later. The ship’s registry was changed from Antwerp to Niue after the transfer and she was beached at Chittagong in February.

The case is a criminal prosecution which of course carries with it a high burden of proof. Seeing as the ship sailed under Belgian flag, the principled application of Belgian and EU law was not as such disputed. Neither do the original owners dispute that at the time of the January 2016 decision, the ship met with the definition of waste ia per CJEU Shell. However defendants argue the EU Waste Shipments Regulation – WSR does not apply for, they argue, the Mineral Water never sailed in European waters and was not physically exported from the EU with a view to recycling (p.5 in fine).

[The court later (p.8) notes this is not quite correct: occasionally EU ports were used for (un)loading and in 2015 there was rare bunkering at Malta].

The court held for the defence. Core to the decision is Article 2, 30 31 and 32: the definitions of ‘import’, ‘export’, ‘transfer’. The prosecutor seeks support in Article 2.22: ”country of dispatch’ means any country from which a shipment of waste is planned to be initiated or is initiated’. The court however held that neither the place of decision nor the flag State is of relevance to the territorial scope of application of the WSR. (Note the contrast on that point with the Ships Recycling Regulation – SRG 1257/2013, not applicable to the facts at issue).

One imagines more on that issue can and should be said upon appeal.

The countries of dispatch, transfer and destination of the ship are all ex-EU. Importantly, at p.8 the court notes there is no indication that the owners would have gamed the system to ensure the ship lay outside EU territorial waters at the time of the decision to discard.

The case shows the importance of the flag State in the SRG (itself not free of difficulties; the IMO Hong Kong Convention should avoid gaming). Of note is also that the place of decision-making (relevant for conflict of laws: locus delicti commissi, eg under A7 Rome II as discussed in Begum v Maran) did not play a  role. The crucial element was the almost complete lack of physical contact between the ship and the EU.

One assumes the prosecution will appeal.

Geert.

Handbook of EU Waste law, 2015, Chapter 3.

Posted on

Safety-Kleen. On the definition of waste and probably not the best use of the Shell authority.

Decisions on the definition of waste under the EU waste framework Directive 2008/98 inevitably involve quite a bit of factual analysis and Safety-Kleen UK Ltd v The Environment Agency [2020] EWHC 3147 (Admin)  is no exception.

Safety-Kleen UK Ltd, the Claimant, provides specialist mechanical parts washers, containing kerosene, to businesses, such as those undertaking automotive repairs and to small engineering businesses. They are used for cleaning the parts of heavy oil, grease, paint, ink, glues and resins. The machines enable a cleaning process by physical means, such as scrubbing and automatic agitation with kerosene, and by kerosene acting as a solvent. Safety-Kleen collects the used kerosene from its customers in drums and replaces it with cleaned kerosene. Safety-Kleen takes the drums of used kerosene back to a depot, empties them into a sump or reservoir and then rinses out the drums with used kerosene from the reservoir, to which the now re-used kerosene returns. From there, the re-used kerosene is pumped into the “dirty” tanks, whence it is tankered away to a different company for a specialised industrial waste recovery or regeneration process, by which the dirty kerosene is distilled and cleaned. The cleaned kerosene is returned to a Safety-Kleen depot, and placed into the cleaned drums.

There was no issue but that the dirty kerosene, when it reached the “dirty” tanks at the depot was “waste”, within the WFD, and remained waste when transferred to the depot for distillation and waste until it was cleaned for re-use by customers. Until 2017, there had been no issue between Safety-Kleen and the Environment Agency but that the used kerosene was waste when it was collected by Safety-Kleen from its customers’ premises. However, in 2017, Safety-Kleen concluded that the kerosene did not become waste until it had been used for the cleaning of the drums back at the depot, and was sent to the “dirty” tanks, to await removal for recovery or regeneration. The Agency thought otherwise.

Ouseley J discussed the classics with particular focus on Arco Chemie and  Shell, and at 50-51 a rather odd deference even in judicial review, to what the regulator itself held. The EU definition of waste is a legal concept; not one to be triggered by the Agency’s conviction. Nevertheless he reaches his ‘own judgment’ (52) fairly easily and, I believe on the basis of the facts available, justifiably, that the kerosene is being discarded by the holder, it being ‘indifferent to what beneficial use Safety-Kleen may be able to make of it back at the depot’ (at 56).

Claimant’s reliance on Shell seemed not the most poignant, seeing as the case here is not one of reverse logistics but rather one of truly spent raw materials on their way to perhaps receiving a second life following treatment.

Geert.

Handbook of EU Waste law, OUP, second ed, 2015.

Posted on

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.

Posted on

Applicable law and statutes of limitation in CSR /business and human rights cases. The High Court, at least prima facie, on shipbreaking in Bangladesh in Begum v Maran.

Update 28 August 2020 permission to appeal and cross-appeal has been granted and is being additionally sought by both parties on various issues.

Hamida Begum v Maran UK [2020] EWHC 1846 (QB) engages exactly the kinds of issues that I have just posted about, in court rather than in concept. On 30th March 2018 Mr Mohammed Khalil Mollah fell to his death whilst working on the demolition of a defunct oil tanker in the Zuma Enterprise Shipyar in Chittagong (now Chattogram), Bangladesh. On 11th April 2019 the deceased’s widow issued proceedings claiming damages for negligence under the UK Law Reform (Miscellaneous Provisions) Act 1934 and the Fatal Accidents Act 1976; alternatively, under Bangladeshi law. The scope of the proceedings has subsequently been broadened inasmuch as draft Amended Particulars of Claim advance a cause of action in restitution: more precisely, unjust enrichment.

Application in the current case is for strike-out and /or summary judgment (denying liability) hence the legal issues are dealt with at prima facie instead of full throttle level. One or two of the decisions deserve full assessment at trial. Trial will indeed follow for the application was dismissed.

The case engages with the exact issues in exchanges I had at the w-e.

Proceedings have not been brought against the owner of the yard and/or the deceased’s employer. Both are Bangladeshi entities. Maran (UK) Ltd,  defendant, is a company registered in the UK and, it is alleged, was both factually and legally responsible for the vessel ending up in Bangladesh where working conditions were known to be highly dangerous.

Focus of the oral argument has been whether claim discloses viable claims in English law on the basis of tort of negligence (answer: yes) and in unjust enrichment (answer: no).

The issue of liability in tort is discussed on the basis of English law, which is odd at first sight given Rome II might suggest as a starting point Bangladeshi law as the lex causae ; Justice Jay himself says so much, but only at 76 ff when he discusses Rome II viz the issue of limitation. In applications for summary judgment however, reasoning and order of argument may take odd form as a result of the prima facie nature of the proceedings and the conversations between bench and parties at case management stage.

On the tort of neglicence claimant argues under English law, with direct relevance to the current debate on environmental and human rights due diligence, that a duty of care required the defendant to take all reasonable steps to ensure that its negotiated and agreed end of life sale and the consequent disposal of the Vessel for demolition would not and did not endanger human health, damage the environment and/or breach international regulations for the protection of human health and the environment. The EU Ship Recycling Regulation 1257/2013 was suggested as playing a role, which is dismissed by Justice Jay at 24 for the Regulation was not applicable ratione temporis.

At 30, claimant’s case on negligence is summarised:

First, the vessel had reached the end of its operating life and a decision was taken (perforce) to dispose of it. Secondly, end-of-life vessels are difficult to dispose of safely. Aside from the evident difficulties inherent in dismantling a large metal structure, a process replete with potential danger, an oil tanker such as this contains numerous hazardous substances such as asbestos, mercury and radio-active components. Although these were listed for Basel Convention purposes and for the attention of the buyer, and the deceased was not injured as a result of exposure to any hazardous substance, the only reasonable inference is that waste such as asbestos is not disposed of safely in Chattogram. Thirdly, the defendant had a choice as to whether to entrust the vessel to a buyer who would convey it to a yard which was either safe or unsafe. Fourthly, the defendant had control and full autonomy over the sale. Fifthly, the defendant knew in all the circumstances that the vessel would end up on Chattogram beach. Sixthly, the defendant knew that the modus operandi at that location entailed scant regard for human life.

The gist of the argument under tort therefore is a classic Donoghue v Stevenson type case of liability arising from a known source of danger.

At 42 ff Justice Jay discusses what to my mind is of great relevance in particular under Article 7 Rome II, should it be engaged, giving claimant a choice between lex locus delicti commissi and lex locus damni for environmental damage, in particular, the issue of ‘control’. One may be aware from my earlier writings (for an overview see my chapter in the 2019 OUP Handbook of Comparative environmental law) that the determination of the lex causae for that issue of control has not been properly discussed by either the CJEU or national courts. This being a prima facie review, the issue is not settled definitively of course however Justice Jay ends by holding that there is no reason to dismiss the case on this issue first hand. This will therefore go to trial.

As noted Rome II is only discussed towards the end, when the issue of limitation surfaces (logically, it would have come first). Claimant does not convince the judge that the case is manifestly more closely connected with England than with Bangladesh under A4(3) Rome II. Then follows the discussion whether this might be ‘environmental damage’ under Article 7 Rome II, which Justice Jay at 83 ff holds preliminarily and prima facie, it is. Analysis of Article 7 is bound to be of great importance at trial and /or appeal.

At 85 a further issue for debate is trial is announced, namely whether the one-year statute of limitation under Bangladeshi law, should be extended under Article 26 Rome II’s allowance for ordre public (compare Roberts and CJEU C-149/18 Martins v DEKRA – that case concerning lois de police and statutes of limitation. 

Plenty of issues to be discussed thoroughly at trial.

Geert.

(Handbook of) European Private International Law, 2nd ed. 2016, Chapter 8, Heading 8.3.

 

 

Posted on

State aid and collective waste recycling bodies. Pitruzzella AG in Société Eco TLC.

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.

Geert.

Handbook of EU Waste law, 2nd ed. 2015 OUP, para 4.116 ff.

 

Posted on

Your regular waste law teaser. Upper Tribunal finds in Devon Waste Management that ‘Fluff’ is not being discarded.

Update 7 May 2021 the Court of Appeal ([2021] EWCA Civ 584) has, justifiably in my view, overturned. Note ia the discussion of language and the meaning of ‘discard.

In [2020] 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.

Geert.

Posted on

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.

 

%d bloggers like this: