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.

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.

 

 

Let them stop eating pollution – The European ban on beaching of EU ships

When teaching International Environmental Law, I tend to at some point in the proceedings have the students ponder Lawrence Summers’ 1992 ‘Let them eat pollution‘ memo. It is a document most wonderful to teach basic economics, internalisation (or lack thereof) of externalities, morality in international trade, comparative advantage etc etc. As well as some history (remember Marie Antoinette, anyone?) and the myths surrounding quotes (qu’ils mangent de la brioche).

The EU have recently decided no longer to let developing countries recycle EU-registered ships through ‘beaching’: basically, one towes a discarded ship, typically with plenty of toxic substances on board or integrated in the ship’s build, unto a beach in a developing country, where subsequently the ship is dismantled without much regard to environmental control of occupational health and safety issues.

The long struggle to regulate the trade is a good example of the challenges of positive harmonisation in international environmental law. For instance, the definition of ‘waste’ as applied to a disused ship long differed between the EU (waste as soon as it is no longer used for its original purpose), the International maritime organisation (no waste as long as it can float) and the Basel Convention (reference to ‘discard’ and to national law). The 2009 Hong Kong Convention aims to address the challenges. This Convention has now been implemented by the EU, who have reportedly ‘gold plated’ it: i.e. the EU have gone beyond what is required under the Convention.

Some details of the scheme may be found here (Irish Presidency of the EU) – the text itself is not yet available. The regime uses a core element of the regime of the Basel Convention on the transboundary shipments of hazardous wastes and their disposal: i.e. employ export authorities in the ‘developed’ world, to only allow exports to ‘developing’ countries when conditions in the latter are deemed sufficiently safe from the workers’ and the environment’s point of view. In the case of the ship recycling regime, this is done by only allowing export of EU-flagged waste ships if they are to be dismantled in facilities that have been approved by the EU.

Plenty of complications remain: this includes the compatibility of the regime with the Basel Convention, and with international trade law; the problem of enforcement and inspection; and the possibility of circumvention by switching flag state.

Geert. Postscript July 2014: the Regulation was eventually adopted as Regulation 1257/2013.

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