Posts Tagged Waste

Protreat: The end of Waste status of Waste lubricating oil; the waste hierarchy; and the absence of duty for Member States to issue regulatory guidance.

Does a Member State have any obligation at all, either generally or in case-specific circumstances, to provide guidance as to when a product derived from Waste lubricating oil – ‘WLO’ has or has not achieved end-of-waste status through either re-refining or reprocessing? And in the case at issue, was the UK’s Environment Agency correct in its classification of the treated WLO as still being waste, specifically: did the Agency unfairly favour waste oils recovery over material recycling?  These were the issues in [2018] EWHC 1983 (Admin) Protreat v Environment Agency in which Williams J evidently looked primarily to EU Waste law, the Waste Framework Directive 2008/98 in particular.

Among the many points of factual discussion is a review of the Member States’ duties under the Waste hierarchy: Protreat argue (at 67) that the Environment Agency, ‘as an emanation of the State, is under a duty proactively to direct its resources and use its powers to seek to ensure the result required by the Waste Directive. It is submitted, too, that the result required includes “the management of waste in accordance with the waste hierarchy set out in Article 4 of the Waste Directive”. According to the Claimant, this requires the Defendant to perform its functions, so far as possible, to ensure that waste oil treatments higher in the waste hierarchy “are more attractive than treatments lower in the hierarchy”‘.

Williams J is entirely correct at para 71 ff to hold that the hierarchy does not imply that its strict application in all circumstances is not always justified: indeed the hierarchy instruct first and foremost the best environmental outcome in specific circumstances.

That in and of itself makes regulatory guidance difficult to issue – and EU law in general does not impose any obligation to do so: at 81: ‘the terms of Article 6 and, in particular, paragraph 4 thereof, do not support the contention that the Directive imposes upon Member States a specific obligation to provide end-of-waste guidance whether in relation to the products of re-refining or the products of any other process of conversion of waste. The power to decide end-of-waste status “case by case in accordance with the case-law” would, no doubt, permit a regulator to issue guidance. I am not persuaded, however, that this language can be the vehicle for the creation of a specific obligation to issue guidance.’ (Sir Wyn also referred to Article 4 and Article 21 to support that analysis).

Reference to Luxembourg was requested but declined.

Geert.

 

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Palin Granit down under. EPA v Grafil Pty and MacKenzie.

There are in fact many differences between Environment Protection Authority v Grafil Pty Ltd; Environment Protection Authority v MacKenzie [2018] NSWLEC 99 and the CJEU’s Palin Granit; and the regulatory context in NSW is quite different from the EU’s. My title therefore is a crowd pleaser rather than legally sound. Yet some of the issues are similar, hence justifying inclusion in the comparative environmental law /waste law binder (and a good teaser for the W-E).

Samantha Daly and Clare Collett have excellent as well as extensive analysis here and I am happy mainly to refer.

Defendants received materials from recycling depots operated by skip bin companies in Sydney. These materials were recovered fines which had been processed and recycled from building and demolition waste, for which there was no market for re-sale at the time (due to the high volumes of such material produced by the recycling industry). This material was trucked to the Premises by transporters from the recyclers and placed in mounds or stockpiles on the Premises.

Was there a stockpile of ‘waste’? Palin Granit considers similar issues in para 36 in particular.

Geert.

 

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

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

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

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

Geert.

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

 

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Arica Victims v Boliden Mineral. Lex causae and export of toxic waste.

‘Reading’ Arica Victims v Boliden Mineral (I have a copy of the case, but not yet a link to ECLI or other database; however there’s a good uncommented summary of the judgment here] leaves me frustrated simply for my lack of understanding of Swedish. Luckily Matilda Hellstorm at Lindahl has good review here (including a hyperlink to her earlier posting which alerted me to the case in 2017).

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, which determined lex causae as lex loci damni. The Court found this to include statute of limitation. This would have been 10 years under Swedish law, and a more generous (in Matilda’s report undefined) period under Chilean law. Statute of limitation therefore following lex causae – not lex fori.

Despite this being good for claimants, the case nevertheless failed. The Swedish court found against liability (for the reasons listed in Matilda’s report). (With a small exception seemingly relating to negligence in seeing waste being uncovered). Proof of causality seems to have been the biggest factor in not finding liability.

Leave to appeal has been applied for.

Geert.

(Handbook of) EU Private International Law, 2nd ed. 2016, Chapter 8.

 

 

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Seatrade: Ships as waste.

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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Thou shallt address landfills of waste tyres. The CJEU in EC v Slovenia.

It is too readily assumed by many that general Member States’ obligations under the EU’s environmental laws are context only, and not really legally binding. In my Handbook of EU Waste law however I report on a number of cases where the European Court of Justice has rebuked Member States for having failed to take measures to attain some of these general objectives. These cases relate to waste law, evidently, however in other cases the Court’s case-law extends this to EU environmental law generally.

One can now add C-153/16 EC v Slovenia to this list. Slovenia had attempted to address the continuation of waste tyres storage and processing at an abandoned quarry, in contravention of an expired environmental permit. The company dug in its heels, ia via prolonged litigation, with storage and processing continuing.

The Court of Justice found that Slovenia had infringed the general duty of care provisions, as well as enforcement obligations of the landfill Directive and the waste framework Directive. (On the related issues with respect to hazardous waste, the Court found the Commission’s infringement proceedings wanting).

Not all that glitters is gold, of course. The direct effect of these general duty of care provisions remains an issue, as does the absence, arguably, in EU law of a duty of care directly imposed upon waste holders and processors. For that, citisens need to pass via national law wich as current case shows, is not always up to scratch.

Geert.

 

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Sjelle Autogenbrug, CJEU defines second hand goods.

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

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

Geert.

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

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