Archive for category Environmental law – EU
The Belgian Council of State (the highest administrative court) has annulled the Flemish waste agency’s export permit in the so-called ‘Slufter’ case, involving large quantities of toxic dredging spoil (for the aficionados: classified as EURAL 17 05 05*; ia with heavy doses of tributyltin – TBT) dredged from the port of Antwerp. The case made by applicants was that the waste would be disposed of in the port of Rotterdam’s ‘slufter’ by way of mere dumping, as opposed to processing ‘at home’ in the Flemish region.
At issue was Article 11 of the Waste shipments Regulation 1013/2006, which allows Member States of export to object to planned shipments of waste destined for disposal. Applicants’ case was that the Flemish waste agency – OVAM should have disallowed the shipment on the basis of the proximity and the self-sufficiency principles. OVAM however pointed out that even if in optimal circumstances, processing in Flanders could lead to higher rates of recovery of the waste, much of it would still simply have to be landfilled. Importantly, it preferred disposal in the Slufter on the basis that the logistics chain was much shorter: load up, transport, dump. As opposed to load up, transport to processing facility for partial recovery (involving three separate processes); load-up of the solid waste left; transport and dump.
The Council of State ruled at the end of May that this decision by OVAM, in particular the reliance of the extent of the logistics chain, lacks proper assessment of the Best Available Technologies for dredging spoil, hence leading to insufficient assessment of the proximity and self-sufficiency principles. The ruling is relevant also with a view to the remainder of the spoil that will continue to be dredged.
For easy of reference (for those wishing to locate copy of the ruling): case numbers are 238220 -238224 included).
Aarhus, Access to Environmental Information Directive. Review of Henney  EWCA Civ 844 .
Department for Business, Energy and Industry Strategy v. Information Commissioner and Henney  EWCA Civ 844 , 29 June 2017 – read judgment
As many will know, there are two different systems of freedom of information, the first and better known, the Freedom for Information Act 2000, and the second, the Environmental Information Regulations 2009. From the perspective of the inquirer (Mr Henney, here), the EIRs are the more favourable, and it was the differences between the systems which gave rise to this long-running dispute to do with energy Smart Meters.
The appeal went in favour of Mr Henney, and the Information Commissioner who had ruled in his favour. But the ultimate case is not resolved, as I shall explain.
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I reported at the time on the General Court‘s decision in Dyson. The CJEU yesterday in Case -44/16P agreed, albeit in less prosaic terms than my earlier post, that the Court’s reasoning was wanting. The case now goes back to the General Court to reconsider those pleas made by Dyson which the Court considers to have been insufficiently answered.
Of most interest to readers of this blog is the argument re proof, science and procedure (at 72 ff): According to the Commission, Dyson does not explain in what way the development of a test with a loaded receptacle would have been more proportionate. The Commission submits that it was not obliged to show that no better test method could be developed, and that it was on the contrary for Dyson to prove that a more appropriate test method existed, which in the view of the General Court it failed to do.
The Court of Justice agrees that the General Court’s entertainment of this question is wanting – the particular parameter was required under the delegating Directive, alleged absence of a reliable test is not enough to ignore it. That is not to say, that upon reconsideration the eventual General Court’s answer may not be the same.
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.
This post should be preceded by a boast alert, but hey: a pat on one’s own shoulder does not hurt once in a while. With Dr Leonie Reins I have written EU Environmental Law, which has now been published by Edward Elgar. The blurb is here. Leonie and I have given a concise yet we hope complete overview of this ever-growing part of EU law. We hope it will please the reader!
I have copy /pasted the TOC below.
We are now turning our attention to (inter alia): EU energy law.
Contents: 1. Setting the context
PART I BASICS/FRAMEWORK OF EUROPEAN ENVIRONMENTAL LAW 2. Principles of European Environmental Law 3. Environmental law making in the European Union 4: Implementation and enforcement Public Participatory Rights 6. Additional tools in implementing European Environmental Law 7. Environmental and Strategic Impact Assessment 8. Environmental Liability and Environmental Crime 9. State Aid and Competition Law
PART II SUBSTANTIVE LEGISLATION 10. Biodiversity and Nature Conservation 11. Water protection legislation and policy 12. Noise pollution legislation and policy 13. Air pollution legislation and policy 14. Climate Change legislation and policy 15. Waste legislation and policy 16. Chemicals legislation and policy 17. Trade and the Environment
There is as yet no EU harmonisation on amino acids, in so far as they have a nutritional or physiological effect and are added to foods or used in the manufacture of foods. A range of EU foodlaws therefore do not apply to national action vis-a-vis amino acids, in particular Regulation 1925/2006 – the food supplements Regulation. In the absence of specific EU law rules regarding prohibition or restriction of the use of other substances or ingredients containing those ‘other substances’, relevant national rules may apply ‘without prejudice to the provisions of the Treaty’.
In C-282/15 Queisser Pharma v Germany, moreover there were no transboundary elements: Articles 34-36 TFEU therefore do not in principle apply.
No doubt food law experts may tell us whether these findings are in any way unusual, however my impression is that the Court of Justice in this judgment stretches the impact of the ‘general principles of EU food law’ as included in Regulation 178/2002. Indeed the Court refers in particular to Article 1(2)’s statement that the Regulation lays down the general principles governing food and feed in general, and food and feed safety in particular, at EU and national level (my emphasis). Article 7 of the Regulation is of particular relevance here. That Article gives a definition of the precautionary principle, and consequential constraints on how far Member States may go in banning foodstuffs, as noted in the absence of EU standards and even if there is no cross-border impact.
Article 7 Precautionary principle
1. In specific circumstances where, following an assessment of available information, the possibility of harmful effects on health is identified but scientific uncertainty persists, provisional risk management measures necessary to ensure the high level of health protection chosen in the Community may be adopted, pending further scientific information for a more comprehensive risk assessment.
2. Measures adopted on the basis of paragraph 1 shall be proportionate and no more restrictive of trade than is required to achieve the high level of health protection chosen in the Community, regard being had to technical and economic feasibility and other factors regarded as legitimate in the matter under consideration. The measures shall be reviewed within a reasonable period of time, depending on the nature of the risk to life or health identified and the type of scientific information needed to clarify the scientific uncertainty and to conduct a more comprehensive risk assessment.
Germany on this point is probably found wanting (‘probably’, because final judgment on the extent of German risk assessment is left to the national court) – reference is best made to the judgment for the Court’s reasoning. It is clear to me that the way in which the Regulation defines precaution, curtails the Member States considerably. Further ammunition against the often heard, and wrong, accusation that the EU is trigger happy to ban substances and processes in the face of uncertainty.