Tag: Directive 2008/98

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Porr Bau: The CJEU encourages the circular economy and resource efficiency in its approach of waste law and excavated, uncontaminated soil.

The Court yesterday held in C-238/21 Porr Bau. I reviewed Medina AG’s Opinion here.

The Court notes ia [27] Austria’s contention that, under Austrian law, where materials are excavated or demolished in the course of a construction project, the main purpose of the construction developer is usually to carry out that project without being hindered by those materials, with the result that they are removed from the site in question with the intention of discarding them.  That sentence already holds the key to the eventual judgment in the word ‘usually’.

The Court like, as I noted, the AG, repeatedly refers to Sappi Austria. [47] following from the various elements considered in Sappi Austria (which itself cross-refers to eg CJEU Shell), the national court is instructed to determine whether the excavated materials constituted a burden which that construction undertaking sought to discard, with the result that there would be a risk that that undertaking would discard them in a manner likely to cause harm to the environment, particularly by dumping them or disposing of them in an uncontrolled manner. [49]:

In the present case, it is apparent from the information before the Court that, even before the excavation of the materials at issue in the main proceedings, local farmers had made an express request for the supply of such materials. After appropriate construction projects had been found, making the requested excavated materials available, that request, it is stated, led to a commitment by Porr Bau to make those excavated materials available, alongside an agreement under which that undertaking would carry out, by means of those materials, the works to adapt and improve the land and cultivation areas duly identified. Such factors, if proven which it is for the referring court to determine, do not appear to be such as to establish the intention of the construction undertaking concerned to discard those materials.

The Court then leaps to an assessment of whether the soil may be considered a by-product under Article 5 WFD, in a logical sequence which I still do not quite get: [50]

It is, therefore, necessary to examine whether the excavated materials at issue in the main proceedings must be classified as a ‘by-product’ within the meaning of Article 5(1) of Directive 2008/98.

It is the ‘therefore’ which I do not understand. If a party does not ‘discard’ the materials which the Court seems to suggest is the case here, then the ‘waste’ definition is not met. There is then no need to consider whether the materials might be ‘by-products’, for this would mean that if the scenario does not meet with the A5 ‘by-products’ definition, they might nevertheless have to be regarded as waste despite the earlier determination of there not being an element of discarding.

The Court nevertheless assesses all A5 criteria leading it strongly to suggest that these products are indeed by-products. It repeats in my view its fallacy of the waste-by products relationship in the dictum of the judgment:

Point 1 of Article 3 and Article 6(1) of Directive 2008/98/EC of the European Parliament and of the Council of 19 November 2008 on waste and repealing certain Directives,

must be interpreted as precluding national legislation under which uncontaminated excavated materials, which, pursuant to national law, are in the highest quality class,

–      must be classified as ‘waste’ where their holder neither intends nor is required to discard them and those materials meet the conditions laid down in Article 5(1) of that directive for being classified as ‘by-products’, and

–      only lose that waste status when they are used directly as a substitute and their holder has satisfied the formal criteria which are irrelevant for the purposes of environmental protection, if those criteria have the effect of undermining the attainment of the objectives of that directive.

It also rebukes the Austrian regime from the point of view of end of waste status, dismissing some of the Austrian requirements for a material to be able to reach that status, as irrelevant and counter-productive to the objectives of the WFD. These requirements are said to be “formal criteria (in particular record-keeping and documentation obligations) which have no  environmentally relevant influence” however neither the CJEU nor the referring court give any further detail.

This is a first chamber, in a five -judge composition. I don’t think it has definitively solved the relationship between ‘waste’ and ‘by-products’.

Geert.

EU Waste law, 2nd ed 2015, 1.20 ff.

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Porr Bau. Medina AG on waste and end-of-waste status of excavated soil.

Medina AG’s end June Opinion in C-238/21 Porr Bau GmbH v Bezirkshauptmannschaft Graz-Umgebung will delight waste lawyers for the case once again evolves around the definition of ‘waste’ as applied to excavated soil. Statute to be interpreted is the WFD or the Waste Framework Directive 2008/98. CJEU SAPPI is a recent judgment  often referred to by the AG.

Porr Bau, the applicant in the main proceedings, is a construction undertaking established in Austria. In July 2015, certain local farmers asked it to supply them, against payment, with excavated soil and to distribute it over their properties. The purpose of the farmers’ request was to level their agricultural land and improve their cultivation areas, thereby increasing yields. Porr Bau applied to the relevant authorities for a statement that the soil was not to be considered waste so as it could avoid a number of taxes. That authority disagreed and also held that the soil, which it considered to be waste, had not yet reached end-of-waste status.

The AG (36) opines that it should not be assumed that all excavated soil by a construction undertaking is by default to be discarded, and that it is difficult to conclude that, under circumstances such as those of the present case, the intention of a construction undertaking is to discard excavated soil that has been carefully selected, subjected to a quality control and supplied as uncontaminated top-quality material in order to attend to a specific request from local operators in need of that material. He also suggests, less convincingly in my view, (38 ff) that such soil may be considered a by-product of the construction sector. 

Should he not be followed on the waste definition issue, the AG suggests and he is right in my view that national law must not deny end-of-waste status until the holder fulfils certain formal requirements with no environmental relevance such as record-keeping and documentation obligations.

Geert.

EU Waste law, 2nd ed 2015, 1.20 ff.

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Sappi Austria: CJEU tries to keep a common sense approach to supporting the circular economy and maintaining the objectives of EU waste law.

Case C‑629/19 Sappi Austria Produktions-GmbH & Co. KG and Wasserverband ‘Region Gratkorn-Gratwein’ v Landeshauptmann von Steiermark in which the CJEU held on Wednesday is in my off the cuff view (I did not research it in the recent case-law) the first case where the CJEU specifically mentions the objectives of the circular economy to support its interpretation of the core definition of ‘waste’ in the Waste Framework Directive 2008/98.

Sappi operate a large industrial paper and pulp production plant in Gratkorn (Austria). On that site is also a sewage treatment plant, operated jointly by Sappi and the Wasserverband, which treats waste water from paper and pulp production as well as municipal waste water. During the treatment of that waste water, which is required by national law, the sewage sludge in question in the main proceedings arises. That sludge is therefore made up of both substances from industrial waste water and substances from municipal waste water. Sewage sludge which is produced in the sewage treatment plant is then incinerated in a boiler of Sappi and in a waste incineration plant operated by the Wasserverband, and the steam reclaimed for the purposes of energy recovery is used in the production of paper and pulp.  hat authority found that, admittedly, the majority of the sewage sludge used for incineration, namely 97%, originated from a paper production process and that this proportion could be regarded as having ‘by-product’ status within the meaning of Paragraph 2(3a) of the AWG 2002. However, that does not apply to the proportion of sewage sludge arising from municipal waste water treatment. That sewage sludge remains waste. Since there is no de minimis limit for the classification of a substance as ‘waste’, the authority assumed that all the sewage sludge incinerated in the industrial plants of Sappi and of the Wasserverband must be classified as ‘waste’.

The CJEU first of all holds that there is no relevant secondary law which provides the kinds of qualitative criteria for sewage sludge to meet with the objectives of the WFD. If there were such laws, and the sludge meets their requirements, it would be exempt form the WFD. It then reminds the referring court, of course, of the extensive authority on the notion of waste (most recently C-624/17 Tronex) yet is happy to provide the national Court with input into the application in casu.

In principle, the sludge is waste, the Court holds: it is a residue from waste water treatment and it is being discarded.

However, the referring judge suggests that the sludge may meet the requirements of A6(1) WFD as being fully ‘recovered’ before it is used in the incineration process. It is there that the CJEU refers to the circular economy: at 68:

it is particularly relevant that the heat generated during the incineration of the sewage sludge is re-used in a paper and pulp production process and that such a process provides a significant benefit to the environment because of the use of recovered material in order to preserve natural resources and to enable the development of a circular economy.

Per C‑60/18 Tallinna Vesi, the recovery of sewage sludge entails certain risks for the environment and human health, particularly linked to the potential presence of hazardous substances. For the sludge at issue here not to be waste, presupposes that the treatment carried out for the purposes of recovery makes it possible to obtain sewage sludge with a high level of protection of the environment and human health, such as required by the WFD, which is, in particular, free from any dangerous substance. For that purpose, it is necessary to ensure that the sewage sludge in question in the main proceedings is harmless (at 66). The CJEU concludes, at 67

It is for the referring court to determine whether the conditions laid down in Article 6(1) of Directive 2008/98 are already met before the sewage sludge is incinerated. It must in particular be determined, as appropriate, on the basis of a scientific and technical analysis, that the sewage sludge meets the statutory limit values for pollutants and that its incineration does not lead to overall adverse environmental or human health impacts.

There are as yet no EU standards for the full recovery of sewage sludge, hence the ball of end of waste status is once again in the Member States’ court.

Geert.

(Handbook of) EU Waste law, 2nd ed. 2015, Oxford, OUP, Chapter 1, 1.149 ff.

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Tronex. Determining ‘waste’ in reverse logistics chains. CJEU supports holders’ duty of inspection, rules out consumer return under product guarantee as ‘discarding’.

I reviewed Kokott AG’s Opinion in C-624/17 OM v Tronex here. The Court yesterday essentially confirmed her Opinion – readers may want to have a quick read of my previous posting to get an idea of the issues.

The Court distinguishes between two main categories. First, redundant articles in the product range of the retailer, wholesaler or importer that were still in their unopened original packaging. The Court at 32: ‘it may be considered that those are new products that were presumably in working condition. Such electrical equipment can be considered to be market products amenable to normal trade and which, in principle, do not represent a burden for their holder.’ However (at 33) that does not mean that these can never be considered to be ‘discarded’: the final test of same needs to be done by the national court.

The second category are electrical appliances returned under the product guarantee. At 43: goods that have undergone a return transaction carried out in accordance with a contractual term and in return for the reimbursement of the purchase price cannot be regarded as having been discarded. Where a consumer effects such a return of non-compliant goods with a view to obtaining a reimbursement of them under the guarantee associated with the sale contract of those goods, that consumer cannot be regarded as having wished to carry out a disposal or recovery operation of goods he had been intending to ‘discard’ within the meaning of the Waste Framework Directive. Moreover per C-241/12 and C-242/12 Shell, the risk that the consumer will discard those goods in a way likely to harm the environment is low.

However such a return operation under the product guarantee does not provide certainty that the electrical appliances concerned will be reused. At 35: ‘It will therefore be necessary to verify, for the purposes of determining the risk of the holder discarding them in a way likely to harm the environment, whether the electrical appliances returned under the product guarantee, where they show defects, can still be sold without being repaired to be used for their original purpose and whether it is certain that they will be reused.’

At 36: if there is no certainty that the holder will actually have it repaired, it has to be considered a waste. At 40 ff:  In order to prove that malfunctioning appliances do not constitute waste, it is therefore for the holder of the products in question to demonstrate not only that they can be reused, but that their reuse is certain, and to ensure that the prior inspections or repairs necessary to that end have been done.

The Court ends at 42 with the clear imposition of a triple duty on the holder (who is not a consumer, per above): a duty of inspection,  and, where applicable, a duty of repair and of packaging.

Geert.

(Handbook of) EU Waste law, 2nd ed. 2015, Oxford, OUP, Chapter 1, 1.149 ff.

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AS Tallinna Vesi: The CJEU on sludge and end of waste.

The Court held today in C-60/18 AS Tallinna Vesi and agrees with its AG re the possibility of national criteria, yet unlike Ms Kokott does not see an obligation in the WFD for the Member States to have a proactive vetting and decision procedure. It does not give much specification to its reasoning, other than a reference to the ‘circumstances of the case’. This may refer, but I am speculating, to applicant wanting the authorities generally to sign off on its production method, rather than requesting an opinion on an individual stream. In other words: fishing expeditions must not be entertained.

If my interpretation is right it underscores what I have remarked elsewhere on the regulatory process, for instance in the case of circular economy: in a grey regulatory zone, we need to think of mechanisms to assist industry in embracing environmentally proactive solutions, rather than driving them into incumbent technologies or worse, illegality. The CJEU’s view is in line with Williams J in Protreat – however I do not think it is the right regulatory path as I also suggest (in Dutch) here.

Geert.

Handbook of EU Waste law, 2nd ed. 2015, OUP, 1.166 ff and 1.189 ff.

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Tronex. Circular economy, reverse logistics qualifying as wastes return to the CJEU. Kokott AG suggests a duty of prompt inspection.

Kokott AG Opined in C-624/17 OM v Tronex end of February (I had flagged the case summarily earlier): whether consumer returns of electrical appliances some of which are no longer usable because defective, and residual stock are to be regarded as waste that may be exported only in accordance with the Waste Shipment Regulation. – Reminiscent of the issues in Shell: in that case in a B2B context.

Tronex’ export consignment that was stopped, consisted of appliances which had been returned by consumers under a product guarantee, on the one hand, and goods which, because of a change to the product range, for example, were or could no longer be sold (normally), on the other. A number of the boxes in which the appliances were packaged carried a notice stating their defects. The glass in some of the glass kettles was damaged. The shipment was to take place without notification or consent in accordance with the Waste Shipment Regulation.

The AG takes a sensible approach which distinguishes between consumer and collector. At 31 ff: The mere fact that objects have been collected for the purpose of reuse does not in itself necessarily support the assumption that they have been discarded. Indeed, it seems sensible, both economically and from the point of view of the efficient use of resources, to make appliances which can no longer be sold on the market for which they were originally intended available on other markets where they may still sell. Particularly in the case of residual stock which is still in its unopened original packaging, therefore, the request for a preliminary reference contains insufficient evidence to support the conclusion that there has been any discarding.

Returned appliances which, on account of serious defects, are no longer usable and can no longer be repaired at reasonable cost, on the other hand, must unquestionably be regarded as waste. Kokott AG suggests waste classification as the default position. At 39: in so far as there are doubts as to the reuse of the goods or substance in question being not a mere possibility but a certainty, without the necessity of using any of the waste recovery processes referred to in the Waste Directive prior to reuse, only the possibility of ‘prompt’ dispelling of the doubt by an inspection of the appliances, can shift the presumption of it being waste.

‘Repair’ is what the AG proposes as the distinctive criterion: at 40: if the inspection shows that the item is still capable of functional use, its status as waste is precluded. The same is true of goods with minor defects which limit functionality only negligibly, meaning that these goods can still be sold without repair, in some cases at a reduced price. At 41: ‘In so far as the inspection identifies defects which need to be repaired before the product is capable of functional use, however, that product constitutes waste, since there is no certainty that the retailer will actually carry out the repair. Whether the repair is less or more expensive cannot be decisive in this regard, since a product that does not work constitutes a burden and its intended use is in doubt.’ The same goes for goods (other than those in the original packaging, per above) which have not been inspected at all.

At 45 ff the AG supports this conclusion with reference to instruction in Annexes to the WEEE Directive. She also suggests that her interpretation, given the criminal law implications, be limited to those instances occurring after the eventual CJEU judgment.

Geert.

(Handbook of) EU Waste law, 2nd ed. 2015, Oxford, OUP, Chapter 1, 1.149 ff.

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French end of waste criteria. Undoubtedly no end to the controversy, though.

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.

Geert.

Handbook of EU Waste law, 2nd ed. 2015, OUP, 1.166 ff and 1.189 ff.

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Tronex: Reverse logistics and waste back at the CJEU.

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.

Geert.

Handbook of EU Waste law, 2nd ed. 2015, OUP, 1.166 ff and 1.189 ff.

 

Question 1

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?

Question 2

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?

Question 3

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?

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AS Tallinna Vesi: Kokott AG on sludge and end of waste.

Case C-60/18 AS Tallinna Vesi could have been, as Advocate General Kokott noted yesterday, about much more. In particular about the exact scope of the Waste Framework Directive’s exclusion for sewage sludge and the relation between the WFD, the waste water Directive and the sewage sludge Directive. However the referring court at least for the time being sees no issue there (the AG’s comments may trigger the applicant into making it an issue, one imagines) and the AG therefore does not entertain it.

Instead the case focusses on whether waste may no longer be regarded as such only if and after it has been recovered as a product which complies with the general standards laid down as being applicable to it? And on whether, alternatively, a waste holder be permitted to request that the competent authorities decide, on a case-by-case basis and irrespective of whether any product standards are in place, whether waste is no longer to be regarded as such.

Ms Kokott emphasises the wide margin of discretion which the Member States have in implementing the Directive. End of waste (‘EoW’) criteria at the national level (in the absence of EU criteria) may not always be warranted particularly in the context of sewage sludge which is often hazardous. However precisely that need for ad hoc assessment should be mirrored by the existence of a procedure for waste operators to apply ad hoc for clarification on end of waste status.

Geert.

Handbook of EU Waste law, 2nd ed. 2015, OUP, 1.166 ff and 1.189 ff.

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Mirror entries in EU (hazardous) waste law. Campos Sánchez-Bordona AG in Verlezza et al. I.a. a useful reminder of the true meaning of precaution.

Update 31 March 2019 the CJEU agrees with its AG. The holder of the waste is required to carry out the relevant internationally recognised tests. Precaution implies that only if after such test which has to be as complete as possible, the presence of hazardous characteristics cannot be clearly established, the hazardous character must be presumed.

Joined Cases C-487/C-489/17 Alfonso Verlezza et al, in which Campos Sánchez-Bordona AG opined  last week, (no version in English available) is one of those rather technical EU environmental law cases which for that reason risks being overlooked by many. This is even more the case in EU waste law. Many of its provisions are subject to criminal law sanctions, hence encouraging defendants to take its application to the most intricate of corners so as to avoid a criminal conviction.

Verlezza et al concerns the implementation by Italy of a notoriously tricky part of EU waste law: the determination of wastes as being ‘hazardous’. Clearly, these wastes are subject to a range of stricter measures than ordinary wastes. Interestingly, while these wastes are more dangerous than ordinary wastes, they are often also more attractive to waste industries: for as secondary raw materials they may have high value (one can think of cartridges, batteries, heavy metals).

Protracted to and fro at the time between the European Commission and the Member States plus Parliament (which I explain in relevant chapter of my Handbook of EU Waste law; which I am pleased to note the AG refers to), eventually led to a regime with two or if one likes three categories: wastes considered per se hazardous; and wastes which may be considered hazardous or not, depending on whether or not they display hazardous properties in the case at issue (hence three categories: hazardous per se; non-hazardous and hazardous in concreto). This latter category are the so-called ‘mirror entries’: wastes originating from the same source which depending on the specifics of the case, may be hazardous or not.

Wastes produced by households (‘domestic waste’) are not considered hazardous. However the AG emphasises correctly that this exemption from the hazardous waste regime (via Article 20 of the waste framework Directive, 2008/98) does not apply to the case at issue, given that the ‘domestic’ wastes concerned have already been mechanically sorted. It is the qualification of the waste residues following sorting that needs to be resolved.

The mirror entries are the result of heated debate between the Institutions. The EC was hesitant to provide a binding list given the need for individual assessment; Council and EP were looking for regulatory certainty. In the end, Member States may (indeed have to)  consider waste as hazardous when the material displays one or more of the hazardous properties listed in Annex to the EU list of waste. This also requires the Member States to issue a procedure which guides this assessment.  It is the specifics of the Italian procedure (producers have to classify specific streams of waste as either hazardous or not; they have to carry out the necessary scientific tests; they are bound by the precautionary principle) which have triggered the case at issue.

At 19 the AG refers to the discussion in Italian scholarship: one part among others on the basis of the precautionary principle defends a reversal of the burden of proof: waste in the mirror entries is considered hazardous unless industry proves its non-hazardous characteristics; the other part proposes that scientific analysis needs to determine hazardousness in each specific case (quoting the sustainable development of the sector in support).

The AG opines that the Italian modus operandi needs to be given the green light, among others referring to the recent April 2018 EC guidance on wastes classification and the criteria defined in the Directive, which render a waste hazardous: producers of waste are perfectly capable indeed in the Directive’s set-up have to assess the hazardous character of the waste and the Italian regulations are a capable way of ensuring this.

The defendants’ ultimate argument that the precautionary principle should allow them to consider waste as hazardous even without such assessment, also fails: scientific assessment is able to determine a substance’s hazardous characteristics.  Defendants’ approach would lead to all mirror entries being defined as hazardous. The Directive’s principle of cost benefit analysis ensures this does not lead to excessive testing-  proportionate testing for properties will do the job. (It may be surprising that the defendants make this argument; but remember: in a criminal procedure all arguments are useful to try and torpedo national law or practice upon which a prosecution is based; without a valid law,, no prosecution).

This latter part of the Opinion, related to the precautionary principle, is a useful reminder to its opponents (who came out in force following this summer’s mutagenesis ruling; for excellent review of which see KJ Garnett here), of the principle’ true meaning.

Geert.

Handbook of EU Waste law, 2nd ed. 2015, OUP, Chapter 2, Heading 2. ff (to which the AG refers).

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