Archive for category Environmental Law – International
Confédération Paysanne, precaution and GMOs. French High Court issues its final ruling taking CJEU findings to their logical conclusion.
A short post to flag the French Conseil d’Etat’s final ruling in which on 7 February it held that organisms obtained via in-vitro mutagenesis techniques should be subject to GMO regulation and that consequently as EurActiv summarise the French authorities must update regulation to include such crops within six months, which includes identifying the agricultural plant varieties which have been obtained by these techniques and subjecting them to the assessments applicable to GMOs.
The ruling follows the CJEU’s mutagenesis finding in C-528/16, reviewed at the time on Steve Peers’ blog here and subsequently by KJ Garnett in RECIEL here. The ruling put agro-bio industry narrators in a spin but in essence is an utterly logical consequence of EU law.
I seem to be having my environment cap firmly on this week so I am happy to thank Le Monde for flagging the judgment of the French Constitutional Court 2019-823 of 31 January in which it sanctioned (against the wishes of applicants, the Union des industries de la protection des plantes, essentially Bayer, Syngenta, BASF) the Government’s ban on the manufacturing of and exportation of pesticides banned for use in France but hitherto available for export, mostly to Africa.
The case I would suggest is one that is also very suited to a business ethics class. Interestingly the Act also mentions that it applies to the degree it is not incompatible with WTO rules – the WTO is not addressed in the judgment.
Applicants’ case is grounded on the freedom of ‘enterprise’ or ‘commerce’, as expressed in the 1789 Déclaration des droits de l’homme et du citoyen – but also the Decret d’Allarde 1791. To the mix of objectives to be balanced, the Court adds the protection of public health (Constitutional recital, 1946) and the Environment Charter 2004, from which the court deduces that environmental protection, as common heritage of mankind, is a Constitutionally ringfenced objective.
At 6 the Court without much ado posits that the French Government in pursuing environmental policy, justifiably may take into account the extraterritorial environmental consequences of activities on French soil.
Having referred to the EU ban on the use of the substances at issue, based on scientific considerations discussed at length in the run-up to the EU law at issue, the Court at 9-10 refers to the principle that it should not overzealous in second-guessing the exercise by Parliament of its balancing exercise. At 11, it notes that the 3-year transitionary period gives corporations ample transitionary time in line with their freedom of commerce.
To the Court, it’s all very much self-evident. For environmental policy and extraterritoriality, its findings are quite relevant.
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.
The mooted Flemish ban on fireworks displays. A concise primer (with referral) on exhaustion, property rights (ECHR) and the internal market (TFEU).
Anyone short of exam essay Qs, consider the planned Flemish ban (with room for local, event-related exceptions) on fireworks displays. Akin to the issues in Ivory Ban or pet collars, at the core of the legal analysis is the legality of use restrictions on goods lawfully marketed in other Member States (see also my brief review of Amsterdam’s booze bikes here).
The exhaustive effect or not of EU secondary law will have to be discussed, as will Article 34 TFEU (including consultation and commissioned research issues and of course proportionality), and indeed A1P1 (Article 1, first Protocol) ECHR.
(For a recent more locally relevant issue, see the Supreme Court’s (Raad van State) December 2019 annulment of an Antwerp highway code rule banning the use of quads and introducing a strict exemption policy).
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.