Archive for category Environmental Law – International
Gloucester Resources: A boon for climate change law and ‘ecologically sustainable development’ in Australia.
Gloucester Resources v Minister for planning  NSWLEC 7 is perfect material for my international environmental law classes at Monash come next (Australian) winter (September). Proposition is a permit for an open cut coal mine. Consent was refused on the basis of 3 reasons: the creation and operation of an open cut coal mine in the proposed location is in direct contravention of each zone’s planning objectives; the residual visual impact of the mine would be significant throughout all stages of the Project; and the Project is not in the public interest. Refusal was evidently appealed.
Preston CJ, the Chief Judge of the Land and Environment Court of New South Wales delivered serious support for an internationally engaged Australian (New South Wales) climate law approach. Although he did cite the Paris Agreement (439 ff: providing context to Australia and NSW’s future challenges; and including an interesting discussion on the balanced measures that might be needed to achieve Australia’s Paris Goals, refuted at 534 ff) and the UNFCCC, he did not need Paris, Kyoto, UNFCCC or anything else ‘international’ to do so. He applied the NSW principle of ‘ecologically sustainable development’ (ESD; a notion which often rings tautologically to my ears).
A blog post cannot do justice to a 700 para judgment – Note the following paras:
At 694 ‘Acceptability of proposed development of natural resource depends not on location of natural resource but on sustainability. One of the ESD principles is sustainable use– exploiting natural resources in manner which is ‘sustainable’ ‘prudent’ ‘rational’ ‘wise’ ‘appropriate’
At 696 ‘In this case, exploitation of coal resource in Gloucester valley would not be sustainable use and would cause substantial environmental and social harm. The Project would have high visual impact over the life of the mine of about two decades. The Project would cause noise, air and light pollution that will contribute to adverse social impacts. Project will have significant negative social impacts; access to and use of infrastructure, services and facilities; culture; health and wellbeing; surroundings; and fears and aspirations…The Project will cause distributive inequity, both within the current generation and between the current and future generations.’
At 514: rejection of the relevance of the limited impact which the project will have on Australia’s GHG emissions overall, with reference to US (EPA v Massachusetts) and the Dutch Urgenda case.
No doubt appeal will follow – a case to watch.
Thank you Paul Davies for signalling the recent French decree on end of waste – EoW criteria. Such national initiatives are seen by some as being a sign of the failure of relevant provisions of EU Waste law (which suggest the EU should be developing such criteria). An alternative reading may suggest that national initiatives may be better places to read the technical and environmental and pubic health safety requirements at the local level, potentially preparing the way for EU criteria. Relevant procedures under EU law arguably are not the most efficient for the initial development of this type of detailed instrument, as the example of plastics and REACH also shows.
Handbook of EU Waste law, 2nd ed. 2015, OUP, 1.166 ff and 1.189 ff.
French Court annuls market authorisation of Roundup. Contrary to public perception, it neither used nor needed the precautionary principle to do so.
In March 2017, France’s ANSES, the relevant food, environment, and occupational health and safety agency, approved Monsanto’s Roundup Pro 360. That authorisation has now been annulled by the Courts at Lyon – around the same time the story broke of extensive unquestioned copy /pasting by regulators of industry dossiers.
At the beginning of its reasoning the court cites France’s environment charter, to which its Constitution refers. The Charter guarantees everyone in its first Article the right to live in a balanced environment and one with respect for human health. Article 5 entails the precautionary principle, with reference (of course) to scientific assessment and proportionality.
Yet this intro is made for dramatic effect only. The judgment is in fact nothing but a straightforward application of risk assessment requirements on the basis of prevention, not precaution, and a simple observation of infringement of EU law.
At 3 (p.7) the court points out the consequences of the relevant EU authorisation regime. Active ingredients such as glyphosate are authorised (or not; and potentially with conditions) by the EU. Applications in wich these substances are used, by the Member States.
France’s Centre International de Recherche sur le Cancer (CIRC) had classified glyphosate as ‘probably carcinogenic’. Its report on same is referred to by the court as a ‘handbook’, based on peer reviewed studies, the data of which are objectively verifiable as well as replicable. In the other corner, one study referred to by Monsanto (at 7). Relevant EFSA studies only look at the active ingredient and it is these studies upon which ANSES’ decision was based. These studies do not assess the active ingredients’ actual use in preparations such as Roundup Pro 360 which is 41.5% glyphosate. Consequently ANSES quite straightforwardly violates Regulation 1107/2009, particularly its Article 36(6), which prescribes that interaction between the active substance, safeners, synergists and co-formulants shall be taken into account in the evaluation of plant protection products.
The judgment is convincing and straightforward. The road to it was all but easy.
EU environmental law (with Leonie Reins), Edward Elgar, soft cover edition 2018, p.28 ff.
Update 19 March 2019 see Quentin Decleve here for the US following suit, related to rule of law /due process/ hearing rights issues before the Korean competition authority.
Update 16 January 2019 the first such trigger was quickly followed by a second: the EU have requested consultations with Ukraine over the country’s ban on the export of unprocessed woods.
This is a short posting for completeness and filing purposes. The EU have requested consultations with South Korea under the Trade and Sustainable Development chapter of the EU-Korea FTA. Labour rights are at the heart of the request. The request is a first trigger of the ‘Trade and’ consultations chapters under recent EU FTAs. I am not in a position to say more at this stage.
I have review of Shell at the CJEU here, and final judgment in Rotterdam here. Next Thursday the hearing takes places in C-624/17 Tronex which echoes many of the issues in Shell. When, if at all, is the definition of waste triggered in a reverse logistics chain: with a focus on the relationships between the various professional parties in the chain (that the consumer is not handling waste when returning a product in these circumstances is now fairly established).
Questions referred are below.
Handbook of EU Waste law, 2nd ed. 2015, OUP, 1.166 ff and 1.189 ff.
1. (a) Is a retailer which sends back an object returned by a consumer, or an object in its product range that has become redundant, to its supplier (namely the importer, wholesaler, distributor, producer or anyone else from whom it has obtained the object) pursuant to the agreement between the retailer and its supplier to be regarded as a holder which discards the object, within the meaning of Article 3.1 of the Framework Directive? 1
(b) Would the answer to Question 1.(1) be different if the object is one which has an easily repairable fault or defect?
(c) Would the answer to Question 1.(1) be different if the object is one which has a fault or defect of such extent or severity that it is, as a result, no longer suitable or usable for its original purpose?
2. (a) Is a retailer or supplier which sells on an object returned by a consumer, or an object in its product range which has become redundant, to a buyer (of residual consignments) to be regarded as a holder which discards the object, within the meaning of Article 3.1 of the Framework Directive?
(b) Is the answer to Question 2.(1) affected by the amount of the purchase price to be paid by the buyer to the retailer or supplier?
(c) Would the answer to Question 2.(1) be different if the object is one which has an easily repairable fault or defect?
(d) Would the answer to Question 2.(1) be different if the object is one which has a fault or defect of such extent or severity that it is, as a result, no longer suitable or usable for its original purpose?
3. (a) Is the buyer which sells on to a (foreign) third party a large consignment of goods bought from retailers and suppliers and returned by consumers, and/or goods that have become redundant, to be regarded as a holder which discards a consignment of goods, within the meaning of Article 3.1 of the Framework Directive?
(b) Is the answer to Question 3.(1) affected by the amount of the purchase price to be paid by the third party to the buyer?
(c) Would the answer to Question 3.(1) be different if the consignment of goods also contains some goods which have an easily repairable fault or defect?
(d) Would the answer to Question 3.(1) be different if the consignment of goods also contains some goods which have a fault or defect of such extent or severity that the object in question is no longer, as a result, suitable or usable for its original purpose?
(e) Is the answer to Questions 3.(3) or 3.(4) affected by the percentage of the whole consignment of the goods sold on to the third party that is made up of defective goods? If so, what percentage is the tipping point?
A short update on the Court of Justice’s ruling in C-151/17 Swedish Match, in which yesterday it upheld the legality of Directive 2014/40’s ban on ‘snus’ and generally on tobacco products for oral consumption. (Sweden is exempt: Article 15(1) of the 1994 Act of Accession).
The Court reaffirms the bite of the precautionary principle; emphasises the ‘gateway effect’ of snus for the young, including intern alia because consumption of snus can be done very discreetly and hence enforcement of an age ban (a suggested alternative) not effective; and the importance of giving precedence to public health over economic profit.
It also, yet again, shows that measures like these do not fall out of thin air because, as proponents of the precautionary principle would suggest, anti-innovation zealots dream up restrictive measures to kill enterprise. Rather, following extensive scientific advice, the ban is a sensible and proportionate measure to take.
EU Environmental Law, with Dr Leonie Reins, 2017, Chapter 2, Heading IV.