Posts Tagged environmental guarantee
Update 18 May 2020 confirmed today by the Court of Appeal in  EWCA Civ 649.
Hot on the heels of yesterday’s post on e-collars, a short note on yet another trade and animal welfare /biodiversity case. In  EWHC 2951 (Admin) Friends of Antique Cultural Treasures v Secretary of State for the environment, food and rural affairs, Justice Jay (‘Jay J’ even though correct might sound a bit too intimate) upheld the UK’s planned ban on ivory trade, stricter than anything in place elsewhere. As a general rule, the Act interdicts the sale of antique worked ivory, that is to say pre-1947 artefacts, unless one of limited exemptions is applicable.
The discussion engages CITES, pre-emption /exhaustion by harmonised EU law, the environmental guarantee of Article 193 TFEU (albeit not, oddly, the issue of notification to the EC), Article 34 TFEU, and A1P1 ECHR.
On uncertainty, Justice Jay refers to the precautionary principle: at 155: ‘we are in the realm of scientific and evidentiary uncertainty, and the need for a high level of protection. §3.1 of the Commission’s 2017 Guidance makes that explicit. Although the evidence bearing on the issues of indirect causation and demand in Far Eastern markets may be uncertain, statistically questionable, impressionistic and often anecdotal, I consider that these factors do not preclude the taking of bold and robust action in the light of the precautionary principle.’
Rosalind English has analysis here and refers even to Edmund de Waal’s novel The Hare with the Amber Eyes which has been on my reading list after my wife recommended it – this is a good reminder.
EU environmental law (with Leonie Reins), Edward Elgar, 2018, p.28 ff., and Chapter 17 (p.308 ff).
Germany v Commission re toys: ECJ confirms that recourse to precautionary principle is no walk in the park.
The ECJ this morning held in Germany v Commission (for context see my earlier posting). On 1 March 2012, the European Commission only partially (and temporarily) granted Germany approval for upholding stricter limits on limit values for lead, barium, arsenic, antimony, mercury, nitrosamines and nitrosatable substances in toys (for the decision, see here).
The ECJ stood with Germany only in its appeal against the EC’s decision on values for lead: this decision was internally inconsistent (acknowledgement of higher public health protection in the German measures while at the same time unfounded (and vague) limitation in time for those German measures). However for all other substances, the ECJ rejected Germany’s appeal. In doing so it emphasises the burden of proof which the precautionary principle implies (often misrepresented by opponents of the principle). The review of the available scientific evidence shows first of all the challenges associated with the different methods employed by Germany cq the EC. The latter’s measures employ migration limits (migration being the amount of toxic substances not just released from the product but effectively absorbed by the human body), while Germany’s measures rely on bioavailability (the amount of chemical substances released from the product and available for human absorption, even if not all of that is necessarily effectively absorbed).
The ECJ supports the room for Member States to have divergent opinions on risk than those of the EC, however, it needs to show that the national measures better protect human health and do so in a proportionate way. The crucial shortcoming in Germany’s proof turned out to be that its exposure scenarios were, in the view of the ECJ, unrealistic (and not supported by further scientific reporting): they imply simultaneous exposure of a child to all possible toy safety Directive scenarios: dry, brittle, powder-like or pliable toy material; AND liquid or stocky toy material; AND scraped-off toy material.
Hum. That such simultaneous exposure should necessarily be unrealistic is of course open to debate. Many of us have tales to tell of children achieving the impossible with toys clearly not designed for the game a child or group of children might at some point concoct . (Reminiscent of the inherently flawed furniture endurance tests displayed by large furniture chains: I have always thought that letting our family loose on the displayed piece of kitchen, bathroom or dining room furniture would be a more realistic test than an engineered testroom).
As often with risk assessment and risk management: the final conclusion almost always remains open to discussion.
Consultancy Ecologic have released a report which they have prepared for the European Parliament. It reviews the impact which the Transatlantic Trade and Investment Partnership (TTIP) might have on the environmental ‘acquis’ of the European Union (the collected body of EU environmental law). A wide range of issues are discussed – best have a look at the report for all the details. Included are the risks associated with standing for private companies under classic BITs, which as I reported earlier, the EC have recently defended.
The report downplays the impact which the TTIP might have on ECJ case-law [‘The Court of Justice of the European Union (ECJ) has consistently held that international trade and investment agreements only have direct effect within the EU in very limited circumstances. Thus, in past ECJ cases, private companies have not normally been able to rely on e.g. WTO law for invalidating an EU action or claiming damages from the EU. This is likely to apply to TTIP as well.’] That I believe is a touch incautious. The ECJ might qualify its case-law, in particular given that the extent of integration of a trade agreement, is part of the reason for the ECJ to reject direct effect. If the TTIP eventually will include the type of deep(ish) integration forecast, the Court might well find it to have direct effect in certain circumstances.
The report suggests the EP keep a close eye on the provisions in the agreement with an impact on environmental law. This includes the type of regulatory co-operation which the TTIP might yield: a focus on process or on outcome, as neatly summarised by Simon Lester. It makes me wonder whether the Agreement might do with an Article 193 TFEU-type ‘environmental guarantee’.
Once more unto the breach – German action against Commission Decision on the Toy safety Directive provides a master class in EU law
Pre-script: this case is now known as Case T-198/12, and on 15 May 2013 the Court by way of interim measure ordered the Commission to grant approval to the German measures in full, at least until such time as a judgment on the substance has been issued. It made specific reference to the precautionary principle. The ECJ eventually held in May 2014.
I have always thought of legislation on, and trade in, toys, as a perfect illustration for many regulatory mechanisms worldwide. Prof Francis Snyder’s work (see e.g. here) is a perfect illustration of same.
This is no different for the general workings, and finer mechanics, of EU law. Once more, the sector hands teachers and practitioners of EU law a perfect illustration of harmonisation techniques, exhaustion (pre-emption) arguments, and judicial review.
On 1 March 2012, the European Commission only partially (and temporally) granted Germany approval for upholding stricter limits on limit values for lead, barium, arsenic, antimony, mercury, nitrosamines and nitrosatable substances in toys (for the decision, see here) [As an aside, it is often said that one should never watch laws and sausages being made. Reading that list of substances, prima facie (only) one might want to add toys to that list]. Germany has announced it will appeal that decision with the Court of Justice of the EU.
I can think of one or two areas for discussion: risk management and migration limits v bioavailability (or the cheese and chalk argument); limits to pre-emption; application of the ‘environmental and health guarantee’ of Article 114 TFEU, including the principle of proportionality. Expect that future judgment to feature in core readers of EU law.