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Súdny dvor Európskej únie·30.9.1999

C-318/98

ECLI:EU:C:1999:468

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Súdny dvor Európskej únie
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61998CC0318

OPINION OF MR COSMAS — CASE C-318/98

OPINION OF ADVOCATE GENERAL COSMAS delivered on 30 September 1999 *

Table of contents

I — Introduction I-4/89

II — Legal framework I-4789

A — Community legislation I - 4789

B — National legislation I - 4792

III — Facts I-4792

IV — Questions referred for a preliminary ruling I - 4794

V — Answers to the questions referred for a preliminary ruling I - 4795

A — Admissibility I - 4795

B — Substance I-4796

(a) The issues raised by the provisions of Directive 91/689 I-4796

(1) Articles 130s and 130t of the EC Treaty I-4796

(2) Directive 91/689 I-4798

(b) The options available to the Court I - 4803

(1) Finding the relevant provisions of Directive 91/689 invalid I-4803

(2) Answering the questions referred for a preliminary ruling irrespective of

the issue of the validity or otherwise of the provisions of Directive 91/689 I - 4806

(i) Answer to the first question I-4806

(ii) Answer to the sixth question I - 4808

(iii) Answer to the second and third questions I-4808

(iv) Answer to the fourth and fifth questions I-4810

(c) Proposed solution I-4810

VI — Conclusion I-4811

* Original language: Greek.

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FORNASAR AND OTHERS

I — Introduction Directive 75/442/EEC, 3 as amended by Council Directive 91/156/EEC. 4

1. In this case the Court is asked to give a preliminary ruling on a series of questions submitted to it by the Pretura di Udine, Sezzionė Distaccata di Cividale del Friuli, which were raised in criminal proceedings against several persons charged with dis­ 3. Directive 75/442, as amended, laid charging hazardous waste onto a waste tip down the Community legislation regarding not licensed for the disposal of such waste. the management (transport, collection, sto­ The questions submitted relate to the rage, tipping, treatment) of waste. For that interpretation of Article 1(4) of Council purpose, it defined certain basic notions, Directive 91/689/EEC of 12 December including 'waste' (Article 1) and set the 1991 on hazardous waste 1 and Council environmental objectives to be pursued by Decision 94/904/EC of 22 December 1994 Member States regarding waste manage­ establishing a list of hazardous waste ment (Article 4). Directive 75/442 also pursuant to Article 1(4) of Council Direc­ established the rules concerning the plan­ tive 91/689/EEC on hazardous waste. 2 ning, authorisation and supervision of waste disposal operations, leaving exten­ sive powers to Member States, including the power to designate the national autho­ rities responsible for the implementation of these provisions (Articles 5 and 6).

I I— Legal framework

4. Under the third recital in the preamble to A — Community legislation Directive 91/689/EEC, 'the general rules applying to waste management which are laid down by Council Directive 75/442/ EEC [...] also apply to the management of hazardous waste'. However, under the 2. The provisions of Directive 91/689 were fourth recital 'the correct management of adopted in the context of the Community hazardous waste necessitates additional, rules on waste laid down by Council

3 —Council Directive 75/442/EEC of 15 July 1997 on waste (OJ 1975 L 194, p. 39). 1 — OJ 1991 L 337, p. 20. 4 — Council Directive 91/156/EEC of 18 March 1991 amending 2 — OJ 1994 L 356, p. 14. Directive 75/442/EEC on waste (OJ 1991 L 78, p. 32).

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more stringent rules to take account of the — any other waste which is considered by special nature of such waste'. a Member State to display any of the properties listed in Annex III. Such cases shall be notified to the Commis- sion and reviewed in accordance with the procedure laid down in Article 18 of Directive 75/442/EEC with a view to adaptation of the list.' 5. Directive 91/689 5is a lex specialis in relation to Directive 75/442, as evidenced by Article 1(3) of Directive 91/689, which refers to the definitions provided for by Directive 75/442 with the exception of 'hazardous waste', which is defined by Article 1(4), 6whereby: 6. Annex I to Directive 91/689 is divided into two parts, Annex LA and Annex LB, respectively listing 18 and 22 categories or generic types of hazardous waste according to their nature or the activity that generated them. Annex II lists 51 constituents of the wastes listed in Annex LB that render them '4. For the purpose of this Directive "hazar- hazardous when they have the properties dous waste" means: described in Annex III. Annex III lists 14 properties of waste that render them hazar- dous.

— wastes featuring on a list to be drawn up in accordance with the procedure laid down in Article 18 of Directive 75/442/EEC on the basis of Annexes I 7. Under the fifth recital in the preamble to and II to this Directive, not later than Directive 91/689, 'it is necessary, in order six months before the date of imple- to improve the effectiveness of the manage- mentation of this Directive. These ment of hazardous waste in the Commu- wastes must have one or more of the nity, to use a precise and uniform definition properties listed in Annex III. The list of hazardous waste based on experience'. shall take into account the origin and The definition of these categories acts as composition of the waste and, where the common denominator for the definition necessary, limit the values of concen- of hazardous waste across the Community. tration. This list shall be periodically reviewed and if necessary [revised] by the same procedure,

5 — That directive replaced Council Directive 78/319/EEC of 8. Council Decision 94/904 established the 20 March 1978 on toxic and dangerous waste (OJ 1978 L 84, p. 43). list of hazardous waste (hereinafter 'the 6 — The preceding directive, Directive 78/319, was autonomous Community list') referred to in the first legislation not legislation complementary to Directive indent of Article 1(4) of Directive 91/689. 75/442/EEC.

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FORNASAR AND OTHERS

To date the Community list has never been particular origin of the waste does not need amended. to be taken into account. 8

11. An individual Member State that clas- sifies a type of waste as hazardous has a duty to notify the Commission and can 9. Following the adoption of that list, a apply the provisions of Directive 91/689 to series of different types of waste is at this type of waste. Furthermore, under present defined as hazardous throughout point 4 of the Annex to Council Decision the Community. These are the categories of 94/904 'in accordance with Article 1(4), waste covered by the first indent of Arti- second indent, of Directive 91/689/EEC, cle 1(4) of Directive 91/689 and appearing any waste other than the ones listed below in the Community list, which was estab- which is considered by a Member State to lished in accordance with the procedure display any of the properties listed in laid down by Article 18 of Directive Annex III to Council Directive 91/689/ 75/442. 7 EEC on hazardous waste is hazardous. All such cases will be notified to the Commis- sion and will be examined with a view to amending the list in accordance with Arti- cle 18 of Directive 75/442/EEC' (emphasis added).

10. However, other categories of waste exist that are only considered hazardous by one or more Member States. These 12. Notification to the Commission of concern the waste referred to in the second waste considered by the competent national indent of Article 1(4) of Directive 91/689, authorities to display those properties that is, waste considered hazardous by the enables the Commission to take such cases competent authorities of an individual into account and adapt the list in accor- Member State on the basis of the properties dance with the procedure laid down by listed in Annex III to Directive 91/689. The Article 18 of Directive 75/442. 9

7 — Under Article 18(1), as amended by Article 1(1) of Directive 91/156, the Commission is to be assisted within the 8 — The properties which render waste hazardous under framework of this procedure by a committee composed of Annex III are the following: 'explosive', 'oxidising', 'highly the representatives of the Member States and chaired by the flammable' and 'flammable', 'irritant', 'harmful·, 'toxic', representative of the Commission. The representative of the 'carcinogenic', 'corrosive', 'infectious', 'teratogenic', 'muta- Commission is to submit to the committee a draft of the genic', substances and preparations which release toxic or measures to be taken. The committee is to deliver its opinion very toxic gases in contact with water, air or an acid, on the draft within a time-limit that the chairman may lay substances and preparations capable by any means, after down according to the urgency of the matter. The Commis- disposal, of yielding another substance, e.g. leachate, which sion is to adopt the measures envisaged if they are in possesses any of the characteristics listed above. The last accordance with the opinion of the committee. If the property is waste characterised as 'ecotoxic'. measures envisaged are not in accordance with the opinion 9 — The Commission reports in its written observations that it of the committee or no opinion is delivered, the Commission has received a large number or notifications from the is to submit to the Council without delay a proposal relating national authorities of the Member States concerning the to the measures to be taken. If the Council has not acted classification of waste as hazardous and will proceed to within a period of three months from the date of referral, update the list for the first time. However, no such the Commission is to adopt the proposed measures. notification was submitted by the Italian Republic.

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B — National legislation 15. Moreover, under Article 50 of Legisla- tive Decree 22/97, collecting, transporting and discharging waste without the appro- priate license constitutes a criminal offence.

13. As the national court explains, Direc- tives 91/156 and 91/689, amongst others, were implemented in Italian law by Legis- lative Decree No 22/97 of 5 February 1997. 10 That Decree repealed a large part Ill — Facts of the previous legislation and in particular Presidential Decree No 915/82, which had transposed into Italian law inter alia, Directive 75/442. 11 The new legislation substituted for the term 'toxic waste' the 16. On March 11 1994, during an inspec- term 'hazardous waste'. tion carried out at the waste tip of the company Verdeindustria Sri, toxic waste was discovered while waste was being discharged. An examination of the docu- mentation subsequently showed that the waste originated from the Fincantieri works at Monfalcone. The waste tip was not licensed for the disposal of such waste.

14. In particular, Article 7(4) of Legislative Decree No 22/97 provides that 'hazardous waste is non-domestic waste specified in the list referred to in Annex D on the basis of Annexes G, H and I'. 12 Annex D reproduces verbatim the Community list 17. The officials carrying out the inspection of hazardous waste adopted by Council noticed a number of tin cans and a drum Decision 94/904 and Annexes G, H and I marked 'ICI polyurethane'. The material correspond to Annexes I, II and III to was seized, samples were taken, and it was Directive 91/689. handed over to the public prosecutor's office as classifiable as toxic-harmful waste within the meaning of Presidential Decree 1 0 — GURI, supplemento ordinario No 33 or 15 February No 915/82. Criminal proceedings were 1997. instituted against those legally responsible 11—Presidential Decree No 915/82 of 10 September 1982, under Article 26 of Presidential Decree GURI No 343 of 15 December 1982, p. 9071. The national court further explains that Legislative Decree 915/82, 13 who were charged with disellar- No 22/97 was subsequently amended by Legislative Decree No 389/97 of 8 November 1997, following which Ministerial Decree No 141/98 of 11 March 1998 ('Reg- ulation laying down rules for the disposal of waste by dumping and for the classification of hazardous waste 13 — Fornasar and his co-defendants state in their written disposed of by dumping') was issued. observations that criminal proceedings were instituted 12 — The reference to Annexes G, H and I was introduced by against two employees of Fincantieri, the head of the Legislative Decree No 389/97. transport company and two waste tip managers.

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FORNASAR AND OTHERS

ging 'toxic and harmful' waste, under the highly dangerous for human health, as even description 'special waste', without a prior very small concentrations of them in the air, permit. of the order of one part per billion, may provoke very serious, and sometimes fatal, asthma attacks. The expert also referred to the difficulty of classifying that substance under the list in Annex D to Legislative 18. In the course of the proceedings, Direc- Decree No 22/97, since those classifica- tive 91/689 and Legislative Decree tions refer to the origin of the waste, which No 22/97, as amended by Legislative according to the national court cannot be Decree No 389/97, entered into force. identified with certainty in this case. Under Article 2 of the Italian Criminal Code, 'no person may be punished for an act which, in accordance with a subsequent law, does not constitute an offence'. There- fore, the national court had to examine whether the conduct of the accused, charged under Article 26 of Presidential Decree No 915/82, which had in the mean- 21. The national court notes that in this time been repealed, constituted an offence case the origin of the waste, and conse- under Article 50 of Legislative Decree quently the identification of the production No 22/97 and in particular whether the process from which it derives, cannot be waste discovered in the Verdeindustria ascertained with certainty. The documenta- waste tip constituted hazardous waste in tion accompanying the waste and the respect of which the waste tip was unli- witness statements show that the entire censed. load of waste taken to the tip came from the Fincantieri Navali Italiani Spa works at Monfalcone. The size of and the multi- plicity of activities carried out at the works make it impossible to establish what use the 19. During the hearing, it became neces- substance might have had. 14 sary to ascertain the nature of the sub- stances contained in the drum and an expert report was commissioned. The expert was required to carry out analyses of the waste and to state whether or not it was classifiable as hazardous waste and whether the origin of the waste was of relevance to that classification. 22. Nor, according to the national court, does the type of substance found in the drum allow for its use to be determined

20. The expert, after analysing the sub- 14 — The national court states that the Fincantieri works have a stance in the drum, ascertained that it number of carpentry workshops, since ships are con- contained diphenylmethane diisocyanate structed there, from the construction of the plate to the construction of the ship in dry dock and the rigging out of ('MDI') and an isomer thereof. Further- the interna] fittings. Fincantieri carries out shipbuilding, mechanical and related activities, including the fitting out, more, the expert stated that isocyanates are repair and demolition of ships.

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OPINION OF MR COSMAS — CASE C-318/98

with certainty in this case because of the Cividale del Friuli, referred to the Court six multiple uses of that substance. 15 questions for a preliminary ruling:

23. First, the national court raises the issue of how Article 1(4) of Directive 91/689 and Decision 94/904 are to be interpreted with ' —For the purposes of classifying waste as regard to the term 'hazardous waste' and hazardous within the meaning of Arti- ask whether or not the list laid down by cle 1(4) of Council Directive 91/689/ Decision 904/94 is exhaustive/binding. 16 EEC and Council Decision 904/94/EC, is it necessary in each particular case to identify the origin of the waste, refer- red to for the purposes of classification by the list of hazardous waste adopted in that decision, or is it sufficient for 24. Secondly, it considers that it is neces- such purpose that, by reason of its sary to ascertain how the procedure for composition, the substance can only be making additions to the list of hazardous used in theory in a given production waste, laid down by the second indent of process, or is derived as a final product Article 1(4) of Directive 91/689, operates from that process? and whether it is possible to envisage automatic additions to the list, with effects extending to a single Member State.

— Is the list adopted by Council Decision 904/94 exhaustive, so that waste which is not referred to in the list, but which IV — Questions referred for a preliminary nevertheless displays the characteristics referred to in Annexes I, II and III to ruling Directive 91/689/EEC, is excluded?

25. To resolve the case pending before it, the Pretura di Udine, Sezione Distaccata di

15 — The national court explains that MDI is a basic substance — If the Court finds that the list of for the production of many synthetic resins, subsequently hazardous waste is not exhaustive, used for the manufacture of parts of motor vehicles, furniture, plastics, coatings, paint components, etc., thus must automatic addition of hazardous having a very broad range of uses for companies operating in different areas of manufacture. waste to the list be deemed to operate 16 — The national court states that Italian legal theory and case- on the basis of Annexes I, II and HI to law tend to regard that listing as exhaustive for the purpose of classifying waste as hazardous. Directive 91/689/EEC?

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FORNASAR AND OTHERS

— For the purposes of Article 1(4), sec- sibility. They contend that the Court of ond indent, of Directive 91/689/EEC, Justice has consistently held 17 that a Com- what procedure must an individual munity directive may not by itself create Member State follow in classifying as obligations for an individual and that the hazardous waste other than that on the Court should firmly restate that principle list adopted by Council Decision since the national court will rule on the 904/94 which exhibits one of the defendants' criminal liability accordingly. characteristics set down in Annex III They also contend that however the Court to the directive? What body is compe- interprets the Community provisions, the tent to make the assessment and sub- national court will apply the national sequently notify the Commission? legislation most favourable to the defen- dants. According to the prevailing view in Italian case-law and legal theory, the acts for which they are being prosecuted no longer constitute an offence under current law. Therefore, the questions referred for a — Can the judicial authorities of an preliminary ruling are essentially a fabri- individual Member State also be cated case aimed at obtaining an interpre- required to notify the Commission? tation that would allow the national court illegally to extend the scope of obligations laid down by criminal law.

— Under Community legislation, is diphe- nylmethane diisocyanate (MDI) to be classified as hazardous waste or not?'

27. Regarding the issues of admissibility, I would first like to point out that while it is true, according to settled case-law, that the Court may not, under Article 177 of the EC Treaty (now Article 234 EC), decide upon V — Answers to the questions referred for the validity, in regard to Community law, a preliminary ruling of a provision of domestic law, as it would be possible for it to do under Article 169 of the EC Treaty (now Article 226 EC), 18 it nevertheless has jurisdiction to supply the national court with an interpretation of Community law on all such points as may enable that court to determine the issue of A — Admissibility

17 — They cite in particular Case C-168/95 Arcaro [1996] ECR I-4705, paragraph 36. 18 — See for example Case C-6/64 Costa v ENEL [1964] ECR 26. Two of the co-defendants in the main 1141 and Joined Cases C-304/94, C-330/94, C-342/94 and C-224/95 Tombesi and Others [1997] ECR I-3561, proceedings raised an objection to admis- paragraph 36.

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the compatibility of rules with Community B — Substance law for the purposes of the case before it. 19

30. The provisions of Directive 91/689 raise certain issues regarding their compat- ibility with Articles 130r (now, after 28. Also, according to settled case-law, 'it is amendment, Article 174 EC) and 130t for the national courts alone, before which (now Article 176 EC) of the EC Treaty the proceedings are pending and which (a). The Court has two options as to the must assume responsibility for the judg- interpretation of these issues (b): it may ment to be given, to decide, having regard either rule that the relevant provisions of to the particular features of each case, as to that directive are invalid or attempt to both the need for a preliminary ruling to answer the questions referred for a pre- enable them to give judgment and the liminary ruling by the national court with- relevance of the questions which they refer out examining the validity of the directive. I to the Court of Justice. A request for a shall attempt to analyse the various aspects preliminary ruling from a national court of the two options before giving my may be rejected only if it is quite obvious opinion on the latter. that the interpretation of Community law or the examination of the validity of a rule of Community law sought by that court bears no relation to the actual nature of the case or to the subject matter of the main action'. 20

(a) The issues raised by the provisions of Directive 91/689

29. I consider that the national court explains the reasons why the replies given by the Court of Justice will help it to resolve the case before it and it does not (1) Articles 130s and 130t of the EC Treaty appear that those replies will bear no relation to the subject-matter of the main action. Therefore, in the light of the above, the questions referred for preliminary rul- 31. Article 130s of the EC Treaty (now, ing are admissible and I would suggest that, after amendment, Article 175 EC) 21 con- the Court proceed to examine them. stitutes the legal basis for Directive 91/689, which was enacted in the context of action taken by the Community to implement the 19 — See for example C-223/78 Grosoli [1979] ECR 2621, objectives set out in Article 130r, concern- paragraph 3, and Tombest, paragraph 36, cited above. 20 — See in particular C-67/91 Asociación Española de Banca Privada and Others [1992] ECR I-4785, paragraphs 25 and 26; Joined Cases C-332/92, C-333/92 and C- 335/92 Eurico Italia and Others [1994] ECR I-711, paragraph 17; 21 — The Greek version of that directive mistakenly states that Case C-62/93 BP Supergas [1995] ECR I-1883; and Article 130r is the legal basis rather than Article 130s, Tombesi, cited above in footnote 18, paragraph 38. which is correct.

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FORNASAR AND OTHERS

ing Community policy on the environment. Court has for that matter recognised the Article 130r describes this policy and estab­ 2 binding nature of this general principle. 3 lishes the criteria and parameters within which Community institutions can inter­ vene to protect the environment.

34. Of particular interest for the resolution of this case is the reference to a specific (negative) manifestation of the precaution­ ary principle. It implies that the compe­ 32. In particular, Article 130r(2), which tence of public authorities to adopt for a lists the general principles of this Commu­ particular purpose the measures deemed nity policy, should be mentioned. It states necessary to avert a risk to the environment 'Community policy on the environment cannot be restricted, particularly where this shall aim at a high level of protection risk has not been ascertained or 'charted' [...]'. In this way, it determines the content by prior regulation. In other words, deter­ of the legislation to be enacted by Com­ mining in advance and in a limitative munity legislature in the sensitive area of manner the circumstances requiring the environmental protection by adopting a intervention of public authorities to avert qualitative criterion. The notion of a high a specific risk to the environment, even if it level of protection — which of course does is impossible to define that risk in advance not oblige the Community legislature to in a concrete manner, would be contrary to seek the highest possible level of protec­ the precautionary principle. tion 2 2 — is binding on the latter and could constitute grounds for the annulment of a Community rule that does not meet that qualitative criterion.

35. Article 130t of the EC Treaty specifi­ cally implements, in the context of envir­ onmental protection, the principle of sub­ sidiarity, which governs Community policy in this field. That article allows Member 33. Under the precautionary principle, States to maintain or introduce more strin­ expressly referred to in Article 130r(2), gent protective measures, even if in doing the Community must take action even in so they deviate from the existing Commu- cases where there is not an existing, but a potential risk to the environment. The 23 — See Case C-157/96 National Farmers Union (1998) ECR I-2211 and the Opinion of Advocate General Tesauro. Also of interest are the Opinions of Advocate General Gulmann, point 28, in Case C-405/92 Mondiet v Arme­ 22 — See, to that effect, G. Dellis 'Κοινοτικό Δίκαιο Περιβάλ­ ment Islais [1993] ECR I-6133 and Advocate General λοντος. Οι διαστάσεις της προστασίας του περιβάλλον­ Fennelly in Case C- 67/97 Bluhme [1998] ECR 8033, τος στην κοινοτική έννομη τάξη' (Community Law of the which clearly indicate that even in the absence of tangible Environment. The extent to which the environment in evidence of an existing risk to the environment the protected in the Community legal order); Athens, Pub. precautionary principle justifies the adoption of protective A.N. Sakkoulas, 1988 (431 pp.), para. 112. Community measures.

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nity protective measures adopted under classified as hazardous. 25 On the contrary, Article 130s, subject to the measures being it adopts two categories of hazardous compatible with the EC Treaty and notified waste. The first category covers waste to the Commission. featuring on a limitative Community list (first indent of Article 1(4) of Directive 91/689). 26 The second category covers waste that is considered hazardous by a Member State, provided that the limitative but widely worded conditions in Annex III to that directive (second indent of Arti- cle 1(4) of Directive 91/689) are met. It (2) Directive 91/689 should be noted that Member States are required to notify the Commission of waste they classify as hazardous pursuant to Annex III to the directive. That waste is

36. Directive 91/689 lays down the specific rules for the correct management of hazar- dous waste in an environmentally safe way. 24 Given that this is the type of waste most likely to present a risk of serious damage to the environment, these rules are more stringent than the rules regarding the management of solid waste, as stated in the fourth recital of the preamble to Directive 91/689. Moreover, the sixth recital of the 25 — It should be remembered that the Commission, in its preamble to Directive 91/689 states that 'it proposal (93/C 271/06) for a Council directive amending Directive 91/689/EEC on hazardous waste (COM(93) 425 is necessary to ensure that disposal and Final, OJ 1993 C 271, p. 16) which was ultimately rejected, had proposed that Member States identify recovery of hazardous waste is monitored hazardous waste on the basis of the criteria in Annexes I, in the fullest manner possible'. II and III to the directive. Thus, the list of hazardous waste would be made indicative rather than binding (fourth and fifth recitals). Moreover, it is significant that Directive 78/319 previously in force, which was adopted under Articles 100 and 235 of the EC Treaty (now Articles 94 EC and 308 EC respec- tively), had defined hazardous waste in a general manner. Specifically, under Article 1(b) 'toxic and dangerous waste' meant 'any waste containing or contaminated by the substances or materials listed in the Annex to this Directive of such a nature, in such quantities or such concentrations as to constitute a risk to health or the environment'. 37. Directive 91/689 aims to regulate the Furthermore, Article 1(1) of the Commission proposal for matter at issue in an exhaustive manner. a Council Directive on hazardous waste (COM(88)391 Final — SYN 145, OJ 1988 C 295, p. 8) submitted to the The Community legislature does not define Council on 16 August 1988, as amended by the European Parliament (Amendment No 30) (OJ 1989 C 158, p. 238) the waste considered hazardous on the states, 'The object of this Regulation is to set minimum common rules for the management of toxic and hazardous basis of a general provision that might waste'. Moreover, under Article 1(2) of the proposal in its have provided an indicative list of the original form, the definition of 'hazardous waste' referred to Annexes I, II and III. In particular, under the third properties under which waste could be indent, 'hazardous' was defined as 'any other waste displaying any of the properties listed in Annex III'. 26 — I would point out that the first recital in the preamble to Council Directive 94/31/EC of 27 June 1994 amending 24 — For a more detailed analysis of the provisions of that Directive 91/689/EEC on hazardous waste, which exten- directive see Nicolas de Sadeleer, Le droit communautaire ded the time-limit for the implementation of Directive et les déchets, 1995, L.G.D.J. and Bruyland, Paris, (671 91/689 by the Member States, expressly refers to the pp); p. 293 et seq. at p. 296 et seq. in particular. establishment of a binding list of hazardous waste.

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considered hazardous only in the territory Annex III to Directive 91/689 but the of the Member State that has classified it as measures adopted by that directive for the such. However, the Commission also protection of the environment did not assesses the extent to which it would be immediately apply cannot be accepted. In appropriate to adapt the abovementioned other words, the fact that national autho- list by adding the waste classified as rities of a Member State ascertain that a hazardous by one or more Member States, type of waste fulfils the criteria of Annex III pursuant to the second indent of Arti- to Directive 91/689 per se, suffices for that cle 1(4) of Directive 91/689, to the list. directive to apply directly, even if that waste has not previously been classified as hazardous under a specific national proce- dure and/or the Commission has not been notified of that classification.

38. The abovementioned Community sys- tem for dealing with hazardous waste that is enacted by Directive 91/689 raises three issues of interpretation regarding its com- patibility with the provisions of the primary Community legislation. These issues will be examined below, in order of increasing 40. Second, the following issue of interpre- legal significance. tation is clearly more significant. The wording of Directive 91/689 implies a contrario that Member States cannot clas- sify waste as hazardous and adopt the appropriate measures where Annex III to the directive does not also apply. In other words, Annex III is the legislative frame- work within which Member States may 39. First, I consider that neither the need to take more stringent measures in relation to classify waste as hazardous in advance nor the existing Community list of hazardous the prior communication of that classifica- waste. In this way, the Community legis- tion by a Member State as abovementioned lature is aspiring to regulate hazardous can be considered essential elements for waste in an exhaustive manner. This solu- recognising such waste as hazardous under tion cannot be accepted, as it would be the directive. 27 Such an interpretation directly contrary to the provisions of Artic- would go directly against the precautionary le 130t of the EC Treaty. Directive 91/689 principle and the principle of preventive may of course provide that within the action. A situation where an individual specific Community system for environ- Member State, acting as a Community mental protection that it creates (the draw- authority and following a specific Commu- ing up of a limitative Community list that nity procedure, could ascertain that a will also be supplemented by contributions particular waste was hazardous under of Member States as abovementioned) Member States are given the opportunity of classifying waste that falls within the 27 — See N. De Sadeleer, op. cit., p. 307. scope of Directive 91/689 and Annex III in

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particular, as hazardous, albeit within the set out in Annex III to Directive 91/689, meaning of that Directive. In that way the then the directive would infringe Article specific Community system for the protec- 130t of the EC Treaty. tion of the environment and dealing with hazardous waste is supplemented. How- ever, this power to classify waste can in no way exclude the competence of Member States, based directly on Article 130t, first to maintain or introduce their own auton- omous definition of hazardous waste 28 42. In any event, if Directive 91/689 is and, secondly, to take the necessary mea- interpreted in the light of Article 130t of sures for the protection of the environment the EC Treaty, it must be recognised that, from hazardous waste. It suffices that the apart from the specific Community system conditions stipulated by Article 130t of the for the protection of the environment from EC Treaty are satisfied, in other words, that hazardous waste established by that direc- the measures concerned achieve a more tive, there is always the possibility of stringent protection of the environment creating an autonomous national system that complies with the other Treaty provi- for protection against hazardous waste sions. under Article 130t. In other words, a Member State that considers the list under the first indent of Article 1(4) of the Directive unsatisfactory has two options. It could, first of all, characterise waste displaying the properties listed in Annex III to the directive as hazardous and notify the Commission, so that the Directive will apply to the waste in question and the Commission will examine the possible adaptation of the list. Under Article 130t 41. Therefore, if it were to be accepted that of the EC Treaty, however, the Member the present Community legislation aimed to State is still able to adopt its own measures restrict the possibility of the Member for more stringent protection of the envir- States' classifying certain waste as hazar- onment from the hazardous waste outside dous and taking measures for the protec- the framework of Directive 91/689. That tion of the environment by requiring the solution is imposed by the subsidiarity competent national authorities of the Mem- principle on the one hand and by the ber States, first, to classify this waste as precautionary principle and the principle hazardous in advance and, secondly, only that preventive action should be taken by to classify waste displaying the properties Community institutions in the field of environmental protection on the other.

28 — This means that under Article 130t of the Treaty, they may classify as hazardous waste that is proven to have certain other properties which scientific research (subsequent or not) has considered hazardous, or increase the scope of the criteria provided to establish whether the properties rendering waste hazardous listed in Annex III are present in waste. For example, Member States may consider that waste is 'corrosive' not only where it is made up of 'substances and preparations which may destroy living tissue on contact', as provided for by Annex III (H8) but 43. Thirdly, the extent to which the above- also where it may simply harm living tissue. Regarding this interpretation, see N. de Sadeleer, op. cit., p. 307 et seq. mentioned specific Community system for

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the protection of the environment from consider that the abovementioned system hazardous waste created by Directive infringes the principles of a high level of 91/689 is compatible with the requirements protection for the environment and the and principles of primary Community law precautionary principle. as formulated by Article 130r of the EC Treaty should be examined. This issue is of great practical significance, particularly where a Member State has not created an independent national system to deal with the issue of hazardous waste but relies exclusively on the Community protection established by that directive. 45. First of all, a system that does not provide for a general prohibition of free disposal of hazardous waste into the envir- onment, a prohibition that presupposes a general definition as to what constitutes 'hazardous waste', cannot be considered to provide a 'high' level of environmental protection. I shall not dwell further on this issue, given that the level of environmental protection achieved is primarily determined through scientific and technical data, which are not available to the Court.

44. I consider that Directive 91/689 does not implement the objectives of Arti- cle 130r of the EC Treaty correctly and in compliance with the requirements of that article and the fundamental principles of Community environmental law. As men- tioned above, that directive creates a spe- 46. I do, however believe that the Court cific system for managing hazardous waste has available to it all the necessary inter- characterised by the following four fea- pretative material to rule on whether the tures: (a) the absence of a general definition provisions of that Directive 91/689 are of hazardous waste and of a general compatible with the precautionary princi- prohibition of the free disposal of hazar- ple and the principle of preventive action. dous waste; (b) the establishment of a On this issue, one can only consider that limitative Community list of hazardous the simple fact that Directive 91/689 waste throughout the Community, to attempts to establish when specific mea- which the provisions of that directive sures should be taken to avert certain risks apply; (c) a provision for supplementing to the environment in an exhaustive man- that list, which remains limitative in any ner — since, even if it were ascertained event; (d) the competence of Member States today that certain waste presented a serious to classify certain waste as hazardous, danger to the environment, the necessary specifically within their territory, provided restrictive measures laid down by that it displays the properties limitatively laid directive could not be applied throughout down in Annex III to the directive. I the Community — suffices for a finding

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that the directive infringes the precaution- which is why Directive 91/689 was adopted ary principle and principle of preventive under Article 130s rather than Article 100a action. These fundamental principles do (now, after amendment, Article 95 EC) of not allow for the situation, which Directive the EC Treaty. 29 Moreover, Directive 91/689 accepts, where, if it is ascertained 91/689 unsuccessfully attempts to combine ad hoc that the free disposal of a given the two, to the extent that, as analysed waste is especially dangerous for the envir- above, the protection it affords the envir- onment, nevertheless the general restrictive onment is insufficient under Article 130r. measures provided for under that directive The combination of environmental protec- cannot be taken, throughout the territory tion with the protection of the financial of the Community, against such disposal interests linked to the disposal, manage- unless the Commission includes the waste ment and movement of hazardous waste in question within the limitative Commu- (which fall under the Community legisla- nity list under the first indent of Arti- tion on the free movement of goods) could cle 1(4), either on its own initiative or at perfectly well be achieved through the the request of the Member States. In my enactment of a general prohibition of free opinion, only the formulation of a general disposal of hazardous waste on the one prohibition of free disposal of any waste hand and an indicative list of the waste hazardous to the environment would be considered by the Community legislature to compatible with the fundamental principles be hazardous at the time of its constitution of primary Community environmental law. on the other.

47. It should also be noted that it is not be possible to contend, in response to the above reasoning, that the formulation of a 29 — The legal basis for Commission Proposal (88/C 295/04) general provision prohibiting the free dis- was Article 100a but the Council regarded Article 130s as the legal basis. See Proposal for a Council Directive on posal of hazardous waste would jeopardise hazardous waste COM(88) 391 Final, cited above, sub- the protection of trade and that the existing mitted by the Commission to the Council on 16 August 1988. system created by Directive 91/689 recon- Also, regarding the question of choice of legal basis (as ciles the protection of the environment with between Article 100a and 130s) see Case C-155/91 Commission v Council [1993] ECR I-939, regarding the ensuring freedom of the market. legal basis of Council Directive 91/156. The Commission considered that the Council erroneously selected Arti- cle 130s rather than Article 100a. The Court rejected the Commission's application, however, holding that Directive 91/156 on waste has as its main object to ensure the effective management of waste with a view to protecting the environment and, accordingly, could be adopted on the sole basis of Article 130s of the Treaty (paragraphs 20 and 21). See also the Opinion of Advocate General Tesauro in the above case. Also on that question of the choice between Article 100a and Article 130s as the legal basis for the adoption of Community legislation concerning the envir- onment (inter alia), see the earlier Case C-300/89 Com- mission v Council [1991] ECR I-2867 together with the Opinion of Advocate General Tesauro. That case con- 48. First, the protection of the legal interest cerned a directive on waste from the titanium dioxide industry and the Court held (paragraph 25) that Arti- of the environment in this case overrides cle 100a should have constituted the legal basis rather than Article 130s, which had been chosen by the Council. the legal interest in the protection of trade,

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(b) The options available to the Court provisions of the Directive 91/689 and the Community list that define hazardous waste and in particular the four above- mentioned features.

49. On conclusion of the foregoing analy- sis, however, the Court is faced with the following dilemma: it could either find Directive 91/689 incompatible with the overriding provisions of Articles 130r and 51. Such a finding would render the rele- 130t of the EC Treaty and consequently, in vant provisions of that directive, as well, of its collateral review of the legality of that course, as the provisions of Decision directive, be led to remove the 'defective' 94/904 and the national legislation that provisions of the latter from secondary introduced these provisions into the Mem- Community legislation (a), or attempt to ber States' legal system inapplicable. In answer the questions referred for a pre- such a case, however, the issue arises as to liminary ruling without touching upon the what the applicable law would be and issue of the directive's validity (b). At first whether there is any leeway for the direct sight, both options present drawbacks. applicability of Article 130r of the EC Should the Court follow the first option, Treaty. that is, find that the provisions in question are invalid, it will be faced with the issue of determining the legislation that would then be applicable to hazardous waste (1). Should it follow the second option, it will be faced with the equally delicate process of giving an interpretation of the directive 52. Before attempting to analyse this issue, compatible with the EC Treaty (2). There- I consider that certain preliminary observa- fore, before presenting my opinion to the tions should be made regarding the out- Court, I shall examine in more detail the come of the questions referred for a pre- aspects of both options. liminary ruling, in view of the changes that would necessarily occur under national law. More specifically, a finding that the abovementioned Community provisions were invalid, and consequently also the national law provisions transposing them into the Italian legal system, would appear to remove the grounds which, according to the order for reference, justified the ques- (1) Finding the relevant provisions of tions referred for a preliminary ruling. In Directive 91/689 invalid other words, once the legislative amend- ment which came into force in the course of the criminal proceedings were to be regar- ded as never implemented, there would, in principle, be no reason to apply Article 2 of the Italian Criminal Code, whereby 'no 50. I would like to point out that a finding person may be punished for an act which, of invalidity can relate only to those in accordance with a subsequent law, does

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not constitute an offence'. Therefore, particularly where the latter have the a should the Court rule that the provisions broad discretion with regard to the choice of Directive 91/689 and Decision 94/904 of the most appropriate technical mea- are invalid as discussed above, there would sures. 30 appear to be no need for an answer to the questions referred by the national court.

55. Nonetheless, in exceptional circum- stances such as this case, it can be accepted that there is a core content in the above 53. However, at this point the question articles of the Treaty which has become arises as to whether the national court is apparent through judicial review of the bound to review the national legal frame- measures already adopted at Community work that would result from a finding that level. This core forms part of the legislative the Community provisions were invalid, in content of those articles and it does not view of the above analysis of Articles 130r appear possible to subvert it by any sub- and 130t of the EC Treaty. I would point sequent provision of secondary Community out that, under Italian criminal law, as well legislation. 31 The possibility of direct as the general principles of criminal law application of the articles of the Treaty is common to all Member States, such review based precisely on that core content, which could affect the course of the criminal in this case concerns the existence of a proceedings pending only to the extent that general prohibition on free disposal of it may be considered to result in a legal hazardous waste and the possibility of situation more favourable to the defendant. drawing up a list of hazardous waste that I shall now attempt to answer the above is only indicative. That direct application of questions by examining whether it is pos- the articles of the Treaty, which is limited in sible for these articles of the Treaty to apply scope, is not contrary to the general directly. requirements for the direct application of the provisions of the Treaty or to the separation of institutional powers as between the Court and the other Commu- nity institutions.

54. At first glance, it would not appear easy to support the view that Article 130r of the EC Treaty could apply directly. First, measures of Community policy established in Articles 130r(2) and 130s appear to be 56. The said core legislative content of technical in nature, and rendered necessary Article 130r can be considered sufficiently for the specification and implementation of clear and specific. As already mentioned, the provisions of Article 130r in the domes- tic law of the Member States. Secondly, even though the Court may declare provi- 30 — See point 49 of my Opinion in Case C-360/97 Nijhuis 11999] ECR 1919. sions of secondary Community legislation 31 — Regarding the issues of altering such a core, see, for to be invalid, it may not assume the role instance Meyer-Bisch (ed.), Le noyau intangible des droits de l'homme, 1991, Editions Universitaires, Fribourg, assigned to the Community institutions, Switzerland.

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there is no doubt that the free disposal of be reformulating the provisions of the waste should be prohibited in all Member invalid directive in accordance with the States. In the specific context in which the aims of the Treaty. Specifically, the Court's issue is raised in this case, that prohibition intervention would result in the addition to constitutes, in a negative manifestation, the the Community system as originally envi- direct consequence of the precautionary saged, to which Directive 91/689 attempted principle and the principle of preventive to give shape, of a general prohibition on action analysed above. the free disposal of hazardous waste on the one hand, and the transformation of the exhaustive Community list into an indica- tive list on the other. 33

57. However, how will hazardous waste be defined? Does such a definition not con- stitute a technical matter within the exclu- 59. Such determination of the elements of sive competence of the Council? It is my the core content of Article 130r of the view that the Court may provide guidelines Treaty would render it directly applicable, for such a definition which will have all the protecting in this case the effectiveness of characteristics stipulated by the Treaty and that Treaty article. At the same time it

slot into the semantic field of the core would enable the Court, abiding by all the provisions, having direct effect, of Arti- technical matters decided upon by the cle 130r. However, the Court may not, in legislative initiative of the competent Com- establishing such a definition (and nor does munity institutions which, despite appear- it need to) act as the initiator of rules. The ing in the provisions of the directive found most appropriate solution would be a to be invalid, cannot be regarded as con- definition based on the elements of the trary to the Treaty, to fill the gap seemingly definition provided by the directive found invalid which, insofar as they do not infringe the Treaty, may be regarded as 33 — That reformulating in essence, of the rules of secondary Community law by the recognition of a core content the technical basis for drawing up both a general definition and an indicative list of protecting social rights is analogous to the standard case- law of national courts when reviewing the constitutionality of legislation. The constitutional provisions that protect hazardous waste. 32 social rights, whilst first and foremost imposing obliga- tions for the State, do not generate actionable claims that are effective in practice against State authorities which have omitted to initiate the procedure to implement those rights, in the sense that the possible invalidity of that omission could not lead to the implementation sought, given the fact that there is no previous regime applicable and the courts may not assume the role assigned to the legislative or administrative authorities.

If, however, those authorities have taken certain measures implementing the constitutional provisions, review on the substance can take place and the possible invalidity of those measures may 58. In practice, in defining the potential form the core of the legislative content, which will have to be respected by any subsequent legislation or regulations. components for the classification of hazar- See my Opinion, in Nijhuis, cited in footnote 30. dous waste as above, the Court would only It is worth emphasising that this is the opposite case to Case C-443/93 Vougioukas [1995] ECR I-4033, where the Court rightly held that it could not make good the Council's omission to take the measures required by Article 51 of the EC Treaty (now, after amendment, 32 — For example, hazardous wastes are wastes that endanger Article 42 EC) regarding the coordination of special human health or the environment because or their origin, schemes for civil servants. Indeed in Vougioukas the Court composition or limit values of concentration of certain could not have undertaken any reformulation, inasmuch as components.

In particular, such wastes are those included the Council had not previously initiated legislation on that in the Community list of hazardous waste. particular matter.

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left by the defects in the secondary Com- view of the rules and principles of the munity legislation until the adoption of national criminal law applicable, is the sole new measures, without unlawfully taking body competent to establish accurately the on a primary legislative role. It should be national law applicable and define the emphasized that in reality this would not be issues requiring interpretation that may filling a legal lacuna but would be the arise with regard to the above determina- recognition required of the core legislative tion of the applicable Community law. In content of Article 130r which is directly the context of that determination, the applicable. national court may again refer questions for a preliminary ruling to the Court if it considers it necessary to do so.

60. It must therefore be accepted that, should the relevant provisions of Directive (2) Answering the questions referred for a 91/689 be found invalid, the national court preliminary ruling irrespective of the issue should apply the national legislation which of the validity or otherwise of the provi- it deems valid — either the previously sions of Directive 91/689 applicable legislation in revived form or the later legislation reformulated in accor- dance with the Community legislation, as reformulated through the 'quasi' direct application of the Treaty articles — once 62. I consider it best to deal with the it has reviewed the national legislation on questions referred for a preliminary ruling the basis of the directly applicable core of in the following order: the first question Article 130r as defined above. 34 will be answered first, then the sixth question. Questions two and three will be answered together, and, lastly, so will questions four and five, this being necessary given that the issues raised are linked.

61. That review falls exclusively within the jurisdiction of the national court, which, in (i) Answer to the first question 34 — In prohibiting measures of secondary Community legisla- tion from preventing any Member State from maintaining or introducing more stringent measures to protect the environment, Article 130t of the Treaty in no way prevents Member States from adopting such measures even where no Community measures have been adopted and, in any 63. By the first question referred for a case, where measures of that type which were adopted initially have been annulled. preliminary ruling the national court seeks

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to ascertain in substance whether Arti- composition of the waste and where appro- cle 1(4) of Directive 91/689 and Decision priate limit values of concentration. 35 94/904 should be interpreted as requiring Therefore, even in the specific context of specific proof that a waste derives from a the directive, origin is not the sole criterion production process or activity included in for classifying waste as hazardous. the Community list of hazardous waste for it to be classified as hazardous or whether the observation that the waste could in theory be used in a given production process or is derived from it as a final product suffices.

66. In any event, in view of Article 130t of the Treaty as interpreted above, the criteria employed by the Community legislature for the classification of certain waste as hazar- dous cannot be binding for Member States in the sense that it must be shown in actual 64. It appears from the wording of Direc- tive 91/689 that the Community legislature 35 — For certain waste to be classified as hazardous under the attached great importance to the origin of system established by Directive 91/689 and Decision the waste, laying down that the process or 94/904 a specific three-stage procedure must be followed. First the origin of the waste must be determined in activity it derived from should be taken accordance with the type of sectoral activity from which it derives, the type of process or the type of waste.

To that into account in classifying it as hazardous. end, recourse must be had to the chapter headings (categories) of the list of hazardous waste published in Decision 94/904. Subsequently, within each chapter head- ing, the specific category takes precedence over the general category regarding the classification of waste as hazar- dous. Within the specific category, the specific definition overrides the general definitions of waste for the classifi- cation of waste as hazardous according to its origin. If the definition of the waste on the basis of its origin is included in the list, the waste is classified as hazardous.

Conversely, if it does not appear in the list, the waste must be examined on the basis not of the chapter headings (categories) pertaining to origin, but of those relating to type of waste, such as those referred to in chapter headings 13 (oil wastes (except edible oils. . .)) and 14 (wastes from organic substances employed as solvents). The specific chapter headings for types of waste include 65. However, the fact that inclusion in the waste that may be classified under several categories/ Community list is initially based on chapter headings according to their origin. If in this case it is impossible to classify waste according to its origin, the waste's origin does not mean that the because of the large number of possible different sectoral origins, ultimately the classification must be made, as precise ascertainment of the waste's origin pointed out by the German Government, not according to sector but according to type of waste, and the waste should is the only decisive factor as regards its be classified under the group whose typical properties it classification as hazardous. This is evi- displays. The German Government uses the example of deposits produced by oil/water separators which are denced by the interpretation of the relevant soaked up by suction vehicles in various operations used in the chemical industry (those operations fall under provisions of Directive 91/689. Under the chapter headings 06 (wastes from inorganic chemical first indent of Article 1(4) the list features processes) and 07 (wastes from organic chemical pro- cesses)) which should be classified under different sectoral waste that meets the conditions of Annex- origins. Because these sludges are collected in only one tank, they cannot be classified under any of the headings es I, II and III to that directive. According regarding origin. They should therefore be classified under to the wording of the list, account is taken heading 13 according to the type of waste (oil wastes, except edible oils), subheading 1305 (oil/water separator not only of the origin but also of the contents), type 130502 (oil/separator sludges).

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fact or theoretically that the waste origi- 69. In any event, in view of Article 130t as nates from a production process or activity interpreted above, Directive 91/689 and found in the Community list of hazardous Decision 94/904 cannot prevent the autho- waste. rities of a Member State from considering other waste hazardous on the basis of properties other than those found in Annex III. In accordance with the fore- going analysis, the national court may seek to ascertain under national law whether MDI can be regarded as hazardous waste, guided by the need for more stringent (ii) Answer to the sixth question protection of human health and the envir- onment in the management of hazardous waste.

67. By the sixth question referred for a preliminary ruling the national court seeks to ascertain whether, under Community law, diphenylmethane diisocynate (MDI) may or may not be classified as hazardous waste. (iii) Answer to the second and third ques- tions

68. I shall first reply with regard to the specific framework of Directive 91/689. First, let us note that MDI is not included in 70. By the second question referred for a the Community list of hazardous waste in preliminary ruling, the national court seeks Decision 94/904. Nonetheless, it is clear to ascertain whether the list adopted under from the second indent of Article 1(4) of Decision 94/904 is exhaustive and binding, Directive 91/689 that Community law is in which case waste not included in the list not opposed to a Member State's classifying is excluded, despite displaying the proper- MDI as hazardous waste provided that it ties set out in Annexes I, II and III to displays one or more of the properties listed Directive 91/689. By the third question, in Annex III to Directive 91/689 which which arises should the answer to the render it hazardous. The experience of second question be negative, the national Member States other than Italy leads to court asks the Court to rule on whether it is the conclusion that this waste satisfies the possible for the Community list to be criteria of Annex III. 36 supplemented automatically on the basis of Annexes I, II and III to Directive 91/689. In other words, the national Court wishes 36 — The Commission states, for instance that the Kingdom or Denmark, relying on the properties listed in Annex III to to ascertain in substance whether it is Directive 91/689, did in fact consider MDI to be hazardous possible for the Community list to be waste and notified the Commission accordingly. The Republic of Austria states in its written observations that adapted without the procedure established it has asked for MDI specifically to be added to the by Article 18 of Directive 75/442. Community list.

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71. According to the Commission, a non- from classifying other wastes not included limitative Community list of hazardous in the list as hazardous. waste would in practice mean that it would be possible to include all wastes that were ascertained to fulfil the requirements of Annexes I, II and III to Directive 91/689. Such verification alone would suffice, and there would be no need to observe the procedure under Article 18 of Directive 75/442. That is why the Commission 74. Specifically regarding the third ques- contends that the Community list is limita- tion, it is worth emphasising the following tive. points. Under the specific system estab- lished by Directive 91/689, there can be no doubt that the different stages of the procedure for adapting the Community list, which is based on the initiative taken by Member States to classify waste as hazardous if it displays one or more of the properties listed in Annex III, are 72. The Austrian Government contends necessary and useful for the correct func- that for technical and scientific develop- tioning of the system. It is true that prior ments to be consistently taken into account classification and notification to the Com- it is necessary to divide the sources for mission, which enables the latter to coordi- entry on the list into two sets, only one of nate the updating of the list at Community which will correspond to the Community level, are essential stages for the dynamic list of hazardous waste. This can also be development of this system. concluded from the terms of the second indent of Article 1(4) of Directive 91/689, because if the list were to be considered exhaustive, that could essentially deprive that provision of any regulatory content.

75. The omission of a Member State to fulfil its obligation of prior classification of waste as hazardous and notification thereof to the Commission could result in the Member State being liable for failing to 73. In the interests of clarity, I would repeat comply with the particular obligations that the answer to the second and third flowing from Directive 91/689. However, questions referred for a preliminary ruling once it is recognised at national level that is founded on the supposition that the waste displays the properties listed in provisions of Directive 91/689 are not Annex HI, the said omission in no way invalid in the light of Articles 130r and prevents the provisions for the protection 130t of the Treaty. On that view, it should of human health and the environment be accepted that, even if the Community adopted by that directive from applying list provided for by the directive is limita- with regard to that waste. To adopt a tive, it does not prevent Member States contrary interpretation would be incompa-

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tibie with the precautionary principle and 78. Article 1(4), second indent, of Direc- the principle of preventive action. tive 91/689 makes no reference at all to the national procedure which a Member State must follow or to the body competent to classify certain waste as hazardous and to notify the Commission accordingly. Since the Community legislature has not laid down rules on this matter, the procedure to be followed and the bodies responsible must be ascertained under national law. In 76. In any event, in view of Article 130t of any case, however, I consider that for the the Treaty as interpreted above, the specific specific system established by that directive provisions of Directive 91/689 regarding to function in the most effective way, the prior classification and notification to the competence of national judicial authorities Commission do not prevent Member States to carry out such assessments and notify the from considering waste as hazardous on the Commission must not be excluded prima basis of their national legislation and facie. applying the relevant provisions for the protection of the environment to it.

(c) Proposed solution (iv) Answer to the fourth and fifth ques- tions

79. In conclusion, in view of the foregoing analysis of the issues raised by the system adopted by Directive 91/689 and the 77. By the fourth question the national options available to the Court if it adopts court asks the Court to rule on what either solution suggested, I consider that it procedure, for the purposes of Article 1(4), is certainly possible to rule that the provi- second indent, of Directive 91/689, an sions of Directive 91/689 at issue are individual Member State must follow at invalid. However, given the facts of this national level in classifying waste as hazar- case and the nature of the questions dous and what body is competent to make referred for a preliminary ruling I consider that assessment, in accordance with that it is not necessary to adopt such a Annex III to the directive, and subsequently radical solution and that the interpretation to notify the Commission. In the fifth given under the second option enables the question it asks the Court whether the Court to provide the required answers to judicial authorities of a Member State are the questions referred by the national court also required to notify the Commission. for a preliminary ruling.

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VI — Conclusion

80. In view of the above, I propose that the Court answer the questions referred to it for a preliminary ruling by the Pretura Circondariale di Udine, Sezione Distaccata di Cividale del Friuli, as follows:

(1) The origin of waste cannot be of decisive importance for the purposes of classifying it as hazardous within the meaning of Council Directive 91/689/ EEC of 12 December 1991 on hazardous waste and Council Decision 904/94 of 22 December 1994 establishing a list of hazardous waste pursuant to Article 1(4) of Council Directive 91/689.

(2) Diphenylmethane diisocynate (MDI) may be classified as hazardous waste under Directive 91/689.

(3) The Community list of hazardous waste adopted by Council Decision 904/94/ EEC is limitative.

(4) In view of Article 130t of the EC Treaty (now Article 176 EC) and provided that the conditions for the application of that article are satisfied, the provisions of Directive 91/689 concerning the prior classification of the waste as hazardous and notification thereof to the Commission do not prevent Member States from classifying waste as hazardous on the basis of their national legislation and applying the relevant provisions for the protection of the environment even where the requirements of Annex III to that Directive are not satisfied or there has been no prior classification or notification to the Commission.

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(5) Article 1(4), second indent, of Directive 91/689 makes no reference at all to the national procedure which a Member State must follow or to the body competent to classify certain waste as hazardous and to notify the Commission accordingly. Since the Community legislature has not laid down such rules, they must be ascertained under national law.

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