Judgment — ECLI:EU:C:2003:91
Date: 2003-02-13
Based on: Treaty establishing the European Economic Community (1957)
Subject matter: Environment;Waste
Concepts: Environment
Procedure: Action for failure to fulfil obligations - successful
Origin: Germany

summary of the German arguments put forward in the reply to the letter of formal notice followed by the Commission's refutation of those arguments. It concludes with the declaration that Germany has infringed Regulation EEC No 259/93 Articles 7(2) and (4). 40. Again, Germany sent a response to the reasoned opinion, repeating its earlier position and referring to the lack of clarity of the reasoned opinion. 41. It may be that the letter of formal notice and the reasoned opinion could have been drafted with greater precision. However it is apparent from the above summary of their contents that the documents gave a sufficient indication of the subject-matter of the dispute as required by the case-law of the Court. The reasoned opinion did not moreover broaden that subject-matter as compared to the letter of formal notice (or the application compared to the reasoned opinion), which would not have been permissible. 42. I accordingly conclude that the action brought by the Commission is admissible. The issues before the Court 43. The Commission submits that the administrative practice of the German Länder in question is contrary to Article 7(2) and (4) of the Regulation: it is clear from Article 7(2) that the competent authorities of the Member State of dispatch may raise objections against the shipment to another Member State of waste for recovery only on the basis of Article 7(4), which does not include the principle of self-sufficiency apparently relied on by the competent authorities of those Länder, on the basis of administrative circulars, in their objections against the shipments of waste. At issue essentially therefore is whether the operation to which the waste in question was to be subject constitutes recovery or disposal. In particular the parties are at odds over the questions whether the Länder were entitled to formulate criteria not to be found in the Community waste legislation in order to distinguish between the two types of operation for the purpose of application of the Regulation, what precisely is meant by Use principally as a fuel or other means to generate energy in head R1 of Annex IIB to the Directive and whether the specific criteria set by the Länder in the present case are lawful in the sense that they correctly reflect criteria inherent in the Directive. I shall consider those issues in turn. Member States' discretion to set criteria 44. Germany submits, first, that the Member States have the power to lay down their own criteria for distinguishing between disposal and recovery operations in cases such as those at issue, given the potential overlap between the disposal operation under D10 Incineration on land and the recovery operation under R1 Use principally as a fuel or other means to generate energy and the lack of further guidance in the Community legislation. 45. Germany refers to several other Member States which have also set criteria for the distinction, in particular by imposing a minimum calorific value (apparently of 5 000 kJ/kg in France, between 9 500 kJ/kg and 15 000 kJ/kg in the Flemish region of Belgium, between 11 500 kJ/kg and 15 000 kJ/kg in the Netherlands and 21 000 kJ/kg in the United Kingdom). 46. It also refers to my Opinion in Tombesi, (37) where I referred to the Member States' need to lay down practical rules and guidelines for the day-to-day application of the Directive providing the necessary degree of legal certainty for individuals and stated: As the Directive stands at present, I think it must to some extent be left to Member States to develop more detailed criteria to apply the term recovery operation to the various situations which may occur in practice. 47. In similar vein Germany refers to the Opinion of Advocate General Tesauro in Commission v Council, (38) which concerned the correct legal basis for Council Directive 91/156 (39) which substantially amended the original version of the Waste Directive. (40) The Advocate General stated: [The Directive] sets out the broad lines of the action which the Member States are to take in order to ensure that waste management within the Community is conducted so as to guarantee protection for the environment and health. However, the Member States remain substantially free to define the content of that action and the means which they employ. ... As regards in particular the conditions of competition, the directive does not ... lay down common rules relating to the activity of waste management, but merely defines the principles by which action by the Member States is to be guided. It follows that each Member State may adopt in subiecta materia the provisions which, in its view, are most appropriate for the purpose of attaining the prescribed objectives. Consequently, the rules on waste disposal and recycling may differ - even to a significant degree - from one Member State to another ... 48. In my view however the situation in Tombesi was different in a material respect from the present case: the question before the Court was whether certain substances including residues from production or consumption cycles constituted waste. In order to approach that question I considered, given the definition of waste in the Directive, that under the Directive the sole question is whether the substance in issue is subject to a disposal or recovery operation within the meaning of Annex IIA or B. (41) Since Italy had imposed additional criteria for the definition of waste which were not mentioned in the Directive, I stated in the paragraph following that relied on by Germany: It is in fact probably unnecessary in the present cases to determine the extent of any discretion left to the Member States since it is clear that the Italian decree-laws which prompted the national courts' questions are inconsistent with the Directive. (42) It is manifest therefore that - unsurprisingly - I was not suggesting that Member States had an unfettered discretion to delimit the notions of disposal and recovery. Where - as in Tombesi and, as I will suggest, as in the present case - national law or practice is manifestly inconsistent with the Directive, the question of discretion becomes irrelevant. 49. As for the statements of Advocate General Tesauro in Commission v Council, it appears from a closer reading of his Opinion that he was considering the framework rules on national waste management proposed by the Directive and not the specific terms there defined: indeed he prefaces his discussion with the words If we now turn to its content, the directive (apart from defining the terms which determine its scope), establishes .... (43) The differences between Member States' practice to which the Advocate General alludes may be taken to concern national policies in the field of waste management, for example to encourage the reduction of waste production and its harmfulness and to encourage the recycling of waste. It must be borne in mind that Commission v Council was a challenge to the legal basis chosen by the Council for Directive 91/156, (44) and hence the discussion focused on the objectives of the legislation. There is nothing in the Opinion - or in the judgment of the Court - to suggest that the Advocate General envisaged Member States applying their own criteria to the disposal and recovery operations described in Annex IIA and IIB to the Directive. 50. Germany also refers to the statement of the Court in ARCO (45) that: In the absence of specific Community provisions on proof of the existence of waste, it is for the national court to apply the provisions of its own legal system in that regard, while taking care that the objective and effectiveness of [the Waste Directive] are not undermined. 51. That proposition cannot however be relevant to the present case given the existence in the Directive of specific Community provisions describing disposal and recovery operations. It may be noted that the Court in the immediately following paragraph stated that what is commonly regarded as waste ... is irrelevant in view of the express definition of waste in Article 1(a) of [the Waste Directive]. Contrary to Germany's view, therefore, the Court's statements in ARCO support the proposition that Member States may not further qualify definitions contained in the Directive. 52. The unacceptable consequences of Member States' being permitted to apply their own criteria in such a way are evident from the diverse minimum calorific values which, according to Germany, certain Member States require of waste in order for its incineration with recovery of heat generated to be classified as a recovery operation under head R1 in Annex IIB to the Directive. As mentioned above, those calorific values range from 5 000 kJ/kg in France to 21 000 kJ/kg in the United Kingdom. The application by different Member States (and possibly different regions in the same Member State) of such wide-ranging thresholds would clearly run counter to the objectives of both the Directive, whose aims include a common terminology ... to improve the efficiency of waste management in the Community, (46) and the Regulation, which is built on the premiss that different Member States will apply the same procedures to waste intended for particular operations. As the Commission points out, if Member States were free to set their own divergent criteria determining which operations were to be classified as recovery operations, the impact of Article 7(4) of the Regulation, which exhaustively lists the cases in which Member States may object to shipments of waste for recovery, (47) would be much reduced. 53. That is not to say that a uniform criterion based on calorific value might not be a useful and workable means of distinguishing between recovery and disposal operations if set at Community level. However it appears that it has not been possible to agree such a criterion to date. 54. Both the Commission and Germany refer to a working document submitted by the Commission to the Technical Adaptation Committee in 1999 (48) pursuant to the Directive, which provides for the amendments necessary for adapting the Annexes to the Directive to scientific and technical progress to be adopted in accordance with a prescribed procedure involving a committee composed of representatives of the Member States. (49) That document put forward a number of suggestions for limiting movements of waste to be incinerated. One of the options considered was the development of criteria for distinguishing more clearly between Incineration on land under head D10 of Annex IIA and Use principally as a fuel or other means to generate energy under head R1 of Annex IIB. One of the criteria discussed was calorific value: it was suggested that a calorific value of 17 000 kJ/kg be used as a limit value. However, it appears that a distinction based on that calorific value was not accepted by the majority of Member States. Use ... as a fuel or other means to generate energy 55. Germany submits that Use ... as a fuel or other means to generate energy in the description in head R1 of Annex IIB to the Directive should be interpreted by reference to the objective of the operation. In order to constitute recovery, therefore, the specific aim of an incineration operation must be that the waste is used as a source of energy. Germany considers that that principle, which underlies the practice of the Länder at issue in the present proceedings, precisely reflects the criterion laid down by the Court in ASA, (50) which is also expressed in terms of the operation's principal objective. 56. The Commission in contrast considers that the decisive factor for the purpose of head R1 of Annex IIB to the Directive is that the waste is used as a fuel. Waste will be used as a fuel only if first its combustion generates thermic energy and second the energy so generated is actually used; the waste being burnt is therefore in fact replacing other sources of energy. If those conditions are not satisfied, there is no use as fuel but simply incineration. The Commission notes that the waste to be shipped consisted of mixed waste to be used as fuel in the Belgian cement industry. The waste is unquestionably to be used in Belgian cement factories in such a way that its combustion generates thermic energy which is actually used, replacing in one case up to one third of the energy from primary sources otherwise used and in the other case all such energy. The waste is accordingly intended to be used as a fuel. With regard to the judgment in ASA, the Commission refers to the Court's statement that the essential characteristic of a waste recovery operation is that its principal objective is that the waste serve a useful purpose in replacing other materials which would have had to be used for that purpose, thereby conserving natural resources. (51) It considers that, in the light of its analysis summarised above, that criterion applied to the present case leads ineluctably to the conclusion that the use of mixed waste in cement factories must be classified as a recovery operation. 57. The Commission's analysis appears to me to be sound. As a matter of common sense and on a natural reading of the description, Use ... as a fuel or other means to generate energy must involve the two criteria the Commission proposes. First, if the incineration of waste does not generate more energy than it consumes - for example because the waste in question is not easily combustible, so that more energy is required to ignite it and/or keep it burning than is generated by the incineration itself - there will be no surplus energy available as a fuel. Second, even if surplus energy is generated the waste cannot be regarded as being used as a fuel or other means to generate energy unless that energy is itself used. The concept of using waste as a fuel or other means to generate energy thus inevitably entails that, to the extent to which it is so used, it replaces energy from primary sources. That is clearly consistent with the notion of recovery. 58. Moreover the principal objective of an incineration operation which is an integral part of an industrial process and which generates surplus energy to be used in that industrial process may be said to be the use of the waste as a fuel. Since the use of waste in such a way will evidently replace other fuel, natural resources will be conserved. So interpreted, the description in head R1 of Annex IIB to the Directive may therefore be seen as an application of the criterion laid down by the Court in ASA, (52) namely that the principal objective of a recovery operation is that the waste serve a useful purpose in replacing other materials which would have had to be used for that purpose, thereby conserving natural resources. As I suggested in my Opinion in that case, the decisive question is whether the waste is used for a genuine purpose: if it were not available for a given operation, would that operation none the less be carried out using some other material? (53) In the case of waste used as fuel for a cement factory, the answer to that question is clearly yes: in the absence of available waste, the factory would still operate using other fuel. 59. It is instructive to contrast the present case with Commission v Luxembourg, (54) another action for infringement which concerns proposed shipments of household waste for incineration with incidental recovery of the energy generated. In my Opinion also delivered today I state that, in the case of waste being incinerated in a plant developed for that purpose, the answer to the question set out above is clearly no: in the absence of available waste, there would be no incineration. In those circumstances it would not be right to describe the operation as recovery simply because, whenever waste is available and incinerated, the heat generated by the incineration is used, wholly or partly, as a means to generate energy. That fact does not of itself make the principal objective of the incineration the use of the waste as a fuel or other means to generate energy. 60. In the present case it appears (55) furthermore that the complaints to the Commission which ultimately prompted the present action for infringement were made by the cement manufacturers. It may be assumed therefore that it was advantageous to those manufacturers that the waste should be shipped, which also suggests that the principal objective of the operations at issue is the use of the waste as fuel. The fact that the cement manufacturers lodged complaints illustrates the adverse consequences both for the free movement of goods and for the Community's environmental policy which would flow from an interpretation of the legislation to the effect that operations such as those at issue were correctly classified as disposal. The Member State of dispatch would then be able - as Germany apparently wishes - to prohibit shipments of the waste on the basis of proximity and/or self-sufficiency; manufacturers in other Member States would be prevented from saving natural resources by using the waste as fuel in an industrial process and thereby contributing to the objective of prudent and rational utilisation of natural resources enshrined in Article 174 EC. 61. As the Court noted in Dusseldorp, (56) it was in order to encourage recovery in the Community as a whole, in particular by the development of the most efficient technologies, that the Community legislature stipulated that waste for recovery should be able to move freely between Member States for processing. Admittedly, the Court added the proviso that the transport should pose no threat to the environment. That proviso cannot however in my view be understood in absolute terms, since virtually all methods of transport currently involve some risk to the environment. I understand the Court rather to have been imposing a balancing exercise. As I noted in my Opinion in that case, the environmental arguments are much more finely balanced where the waste to be shipped is for recovery than where it is for disposal: while the transport of waste over distance may, depending on the type of waste, entail certain environmental risks, a single market in waste for recovery is likely to improve recycling, thereby reducing the volume of waste for disposal and conserving primary raw materials. (57) 62. Again the contrast with Commission v Luxembourg is useful: in that case, where the objective of the operation at issue is primarily to dispose of the waste, it seems reasonable that the imperative of environmental protection should override the imperative of the free movement of goods, whereas in the present case, where the objective is to use the waste to fuel a manufacturing process thus sparing natural resources, the converse is true. Quantitative criteria - the meaning of principally 63. Even though it is not in my view lawful for Member States to superimpose further criteria on the description of the recovery operation in head R1 of Annex IIB to the Directive, Use principally as a fuel or other means to generate energy, Germany's submissions as to the lawfulness of the criteria it has laid down remain potentially relevant since it considers that the criterion of minimum calorific value correctly translates the requirement of principal use. It submits that the concept of principal use requires that the principal objective of the operation be the recovery of energy. A use in which the waste is not principally used as a fuel but simply burned does not suffice: in order for the definition in head R1 to be satisfied, the greater part of the waste must be used as a source of energy. According to Germany's calculations, that occurs in general only when the calorific value of 11 000 kJ/kg is reached. Almost all incineration operations make some further use of the heat released: if that fact alone meant that the operation were recovery, virtually all incineration would be recovery. 64. The Commission repeats that the only quantitative element in the definition in head R1 is the requirement that the waste must be principally used, which means that the greater part of the waste must be used as fuel. An operation in which only a minor portion of the waste is burned with use of the heat generated, while the major portion is recovered in another way, would not therefore be classified under head R1 of Annex IIB to the Directive. 65. The Commission's view to my mind is consistent with the wording of Annex IIB. All the language versions of head R1 reflect the requirement that the use must be principally as a fuel or, in slightly different words, that the principal use must be as fuel. If only a minor portion of a consignment of waste is burned with use of the heat generated, the operation evidently cannot be regarded as constituting use principally as a fuel or other means to generate energy. In order to fall within the description in head R1, the consignment as a whole must be principally used. 66. Germany objects that the effect of that interpretation is that an operation will constitute recovery provided that a mere 51% of the waste is to be burned and the energy generated is to be used. It is not however the case that the Member State of dispatch must authorise all shipments of waste intended for such an operation. If the unincinerated portion of the waste is not itself to be recovered, the Member State of dispatch may be entitled to object to its shipment on the basis of the fifth indent of Article 7(4)(a) of the Regulation, which concerns the situation where the ratio of the recoverable and non-recoverable waste, the estimated value of the materials to be finally recovered or the cost of the recovery and the cost of the disposal of the non-recoverable fraction do not justify the recovery under economic and environmental considerations. The Member State of dispatch will be in a position to make such an assessment since in accordance with the Regulation the consignment note must include information with regard to the planned method of disposal for the residual waste after recycling has taken place, the amount of the recycled material in relation to the residual waste and the estimated value of the recycled material. (58) 67. As discussed above, waste can be regarded as used as a fuel or other means to generate energy only where the operation results in a net production of energy and that energy is actually used. The requirement that the waste be principally used as such applies in my view to both those elements of the definition. Thus not only must the greater part of a consignment of waste be burnt in a given incineration operation, the operation will not be recovery unless the energy generated is itself principally used. 68. Provided that those conditions are satisfied, it seems to me that the requirements of head R1 in Annex IIB to the Directive are met and the operation will be a recovery operation. There is thus no need for presumptions involving the calorific value of the waste etc. As the Court stated in ASA (59) in the context of the correct classification of the deposit of waste in a disused mine, the competent authorities must assess proposed shipments of waste on a case-by-case basis. That principle appears to me to be equally applicable in cases such as the present: in order to determine whether the conditions discussed above are satisfied with regard to a given shipment of waste, the authorities will inevitably have to assess each case individually. The use of general presumptions however clearly conflicts with such an approach. The status of mixed waste 69. Germany submits that, in order to determine whether mixed waste is to be genuinely recovered, the qualities of the constituent individual wastes must be considered and not the mixture itself. (60) That, it states, accords with the practice of the majority of the Member States. Germany argues that if mixed waste includes waste the incineration of which could not be regarded as a recovery operation either because it would not if burned alone generate surplus heat or because it would not burn at all, the incineration of that mixed waste cannot be so regarded either but is correctly to be classified as disposal. That point is illustrated by the example given by Germany: various sludges (sludges from cleaning tanks and washing vats, colorant and shellac sludges and phenol sludges) contained in the mixed waste at issue consist of at least 75% water, which does not burn, but evaporates because it is combined with inflammable substances which burn at a temperature sufficient to heat water. Germany argues that the incineration of individually uninflammable waste is not therefore a means to generate energy but on the contrary uses the energy generated by the other waste with which it is combined. 70. In my view however that argument does not take the matter much further: if in fact there is a net energy gain from the incineration of mixed waste and that energy is recovered, the operation is a recovery operation in accordance with head R1 of Annex IIB to the Directive. I do not see why that conclusion should be different merely because individual constituent parts of the waste would, if burned separately, not react in the same way. What is relevant is that the less inflammable waste, as a result of being mixed with more inflammable waste, in fact burns and the energy generated by the combined incineration is used. 71. Germany adds that if it is sufficient that the mixture alone, rather than the component elements, satisfy the definition of the operation in head R1 of Annex IIB to the Directive, the strict separation laid down by the Regulation between waste intended for disposal and waste intended for recovery would become impossible: all waste in fact unsuitable for use as a fuel and hence fit only for disposal could be simply mixed with waste which was so suitable; the first waste would thereby also be regarded as for recovery and thus escape the provisions of the Regulation applicable to waste for disposal. That argument however is also flawed: if those wastes not incinerable on their own are mixed with other, more inflammable, waste and the resulting mixture is in fact to be used principally as a fuel, it is surely appropriate that a shipment of such a mixture should be treated as a shipment of waste for recovery. 72. I accordingly do not accept Germany's submission that components of mixed waste must be assessed individually in order to determine whether the operation to which they are intended to be subjected is a recovery or a disposal operation. Waste containing hazardous or harmful elements 73. Germany submits that, to the extent that components of the mixed waste constitute hazardous waste within the meaning of Council Directive 91/689/EEC on hazardous waste, (61) mixing them with other waste is contrary to Article 2(2) of that directive, which provides: Member States shall take the necessary measures to require that establishment[s] and undertaking[s] which dispose of, recover, collect or transport hazardous waste do not mix different categories of hazardous waste or mix hazardous waste with non-hazardous waste. 74. However, mixing waste contrary to the provisions of Directive 91/689 cannot affect the meaning of recovery and disposal for the purpose of the Waste Directive and of the individual operations listed in Annex IIA and IIB thereto. That view is supported by Article 1(3) of Directive 91/689, which states that the definition of waste and the other terms used therein - which include recovery and disposal - are to be those in the Waste Directive. 75. If Germany has reason to fear that hazardous and non-hazardous wastes are being mixed contrary to the terms of the Hazardous Waste Directive, it must take the necessary measures as required by that directive to ensure that such practices are brought to an end. 76. The criteria laid down by the Länder concerned include the nature and quantity of polluting substances in the waste mixture: if the concentration of certain substances is above a prescribed threshold, incineration of the waste will be regarded as disposal. Germany explains first that this is because - as is clear from the note introducing Annex IIB to the Directive (62) - recovery operations must be harmless and compatible with the environment. However since the note introducing Annex IIA (63) governing disposal is in identical terms, that criterion alone cannot help to distinguish recovery and disposal operations. 77. Germany adds that the network of disposal installations required to be established by the Directive must enable waste to be disposed of by means of the most appropriate methods and technologies in order to ensure a high level of protection for the environment and public health in accordance with Article 5(2) of the Directive. Recovery installations on the other hand do not always have in all Member States an equivalent level of technology. Member States may therefore impose a criterion of harmful content to distinguish between waste for disposal and waste for recovery and hence to ensure that waste containing harmful substances is disposed of in accordance with Article 5(2). 78. I cannot accept that argument. 79. First, Article 4(1) of the Directive imposes a general requirement on Member States to take the necessary measures to ensure that waste is recovered or disposed of without endangering human health and without using processes or methods which could harm the environment; again, therefore, there is no basis for a distinction between waste for recovery and waste for disposal by reference to different levels of environmental regulation of recovery and disposal operations. 80. Second, harmonised standards for air pollution from waste incineration plants are set throughout the Community, currently by Directives 89/369 (64) and 89/429, (65) to be replaced in due course by Directive 2000/76. (66) In those circumstances, Germany cannot prevent the shipment of waste on the basis of alleged lesser compliance with those norms by other Member States. (67) That applies even though Germany may in accordance with the Directives and Article 176 EC maintain or introduce measures for the protection of the environment more stringent than those there laid down: (68) the Court has recently ruled that a Member State may not subject the shipment of waste for disposal to the condition that the intended disposal satisfy the requirements of the environmental protection legislation of the Member State of dispatch, (69) and it is clear from the terms of that judgment and the scheme of the Regulation that that principle will apply a fortiori to any analogous objection to the shipment of waste for recovery. 81. Third, the Court made it clear in ASA (70) that it does not follow from ... the Directive that the hazardous or non-hazardous nature of the waste is, of itself, a relevant criterion for assessing whether a waste treatment operation must be classified as recovery. There is nothing to suggest that that proposition will not be equally applicable where it is the allegedly harmful nature of individual components of mixed waste, rather than the fact that the waste as a whole is hazardous waste, which is at issue. 82. Finally, the Directive itself envisages that waste destined for recovery may contain dangerous substances: the third indent of Article 3(1)(a) requires Member States to take appropriate measures to encourage the development of appropriate techniques for the final disposal of dangerous substances contained in waste destined for recovery. 83. For those reasons also I cannot accept Germany's further argument that, since certain other Community waste instruments regulate the extent to which specific types of harmful waste may be recovered rather than disposed of, the harmful content of individual components of mixed waste is a lawful general criterion which Member States may impose for distinguishing between waste for disposal by incineration and waste for recovery by use as a fuel. 84. I accordingly do not accept that the hazardous or harmful nature of elements of mixed waste is relevant to determining whether the waste should be classified as waste for recovery or waste for disposal. Conclusion 85. I am accordingly of the opinion that the Court should: (1) declare that, by raising objections on the ground of self-sufficiency in the disposal of waste to shipments of waste to other Member States to be used principally as a fuel, the Federal Republic of Germany has failed to fulfil its obligations under Article 7(2) and (4) of Council Regulation (EEC) No 259/93 of 1 February 1993 on the supervision and control of shipments of waste within, into and out of the European Community; (2) order the Federal Republic of Germany to pay the costs. 1: - Original language: English. 2: - OJ 1993 L 30, p. 1. 3: - OJ 1975 L 194, p. 39, as amended by Council Directive 91/156/EEC of 18 March 1991, OJ 1991 L 78, p. 32, and by Council Directive 91/692/EEC of 23 December 1991, OJ 1991 L 377, p. 48. 4: - Article 1(e). 5: - Article 1(f). 6: - As adapted by Commission Decision 96/350/EC of 24 May 1996 adapting Annexes IIA and IIB to Council Directive 75/442/EEC on waste, OJ 1996 L 135, p. 32. 7: - Which requires Member States to take the necessary measures to the same effect. 8: - Case C-187/93 Parliament v Council [1994] ECR I-2857, paragraph 26 of the judgment. 9: - Article 2(i) and (k). 10: - As adapted by Commission Decision 94/721/EC of 21 October 1994 adapting, pursuant to Article 42(3), Annexes II, III and IV to Council Regulation (EEC) No 259/93 on the supervision and control of shipments of waste within, into and out of the European Community, OJ 1994 L 288, p. 36. 11: - Recital 14 in the preamble to the Regulation. 12: - Articles 1(3) and 11 of the Regulation. 13: - Article 2(g). 14: - And, if relevant, of transit. 15: - Articles 3(1) (waste for disposal) and 6(1) (waste for recovery). 16: - Articles 3(3) and 6(3). 17: - Articles 3(4) and 6(4). 18: - Articles 3(5) and 6(5), first and fifth indents. 19: - Article 6(5), sixth, seventh and eighth indents. 20: - And, if relevant, of transit. 21: - Articles 4(1) and 4(2). 22: - And, if relevant, of transit. 23: - Where the waste is listed in Annex IV or has not been assigned to Annex II, III or IV, the competent authorities concerned must give their consent in writing (Article 10). 24: - Article 7(1) and (2). 25: - Article 4(2)(c). 26: - Article 4(3)(a)(i). 27: - Article 4(3)(b)(i). 28: - Article 7(2). 29: - Article 7(4)(b) concerns the objections which may be raised by the competent authorities of transit, not relevant to the present case. 30: - Case C-203/96 [1998] ECR I-4075, paragraphs 33 and 34 of the judgment. 31: - Case C-6/00, paragraph 69 of the judgment delivered on 27 February 2002. 32: - Paragraph 36 of the judgment. 33: - In fact at the time of the circulars, Annex IIB to the Directive had not been adapted by Commission Decision 96/350, cited in note 6. The operation now described under head R1 was then mentioned under head R9; in the German version, moreover, although not in the French or English, the wording was Use as a fuel (other than in direct incineration). Germany however refers throughout its pleadings to the current version of Annex IIB, recognising that the difference in the two German versions was the result of a drafting error. 34: - Case C-365/97 Commission v Italy [1999] ECR I-7773, paragraph 23 of the judgment. 35: - Case 211/81 Commission v Denmark [1982] ECR 4547, paragraph 8 of the judgment. 36: - Joined Cases 142/80 and 143/80 Essevi and Salengo [1981] ECR 1413, paragraph 15 of the judgment. 37: - Joined Cases C-304/94, C-330/94, C-342/94 and C-224/95 Tombesi [1997] ECR I-3561, paragraph 56 of the Opinion. 38: - Case C-155/91 [1993] ECR I-939, paragraphs 8 and 9 of the Opinion. 39: - Cited in note 3. 40: - Directive 75/442, cited in note 2. 41: - Paragraph 57 of the Opinion. 42: - Ibidem. 43: - Paragraph 8; emphasis in original. 44: - Cited in note 3. 45: - Joined Cases C-418/97 and C-419/97 ARCO Chemie Nederland [2000] ECR I-4475, paragraph 70 of the judgment. 46: - See the third recital in the preamble to Directive 91/156, cited in note 3. 47: - ASA, cited in note 31, paragraph 36 of the judgment. 48: - 28 January 1999, XIE3/KW D(99). 49: - Articles 17 and 18. 50: - Cited in note 31, paragraph 69 of the judgment. 51: - Paragraph 69 of the judgment. 52: - Cited in note 31, paragraph 69 of the judgment. 53: - Paragraph 86. 54: - Case C-458/00, paragraph 42 of the Opinion. 55: - According to Germany's representative at the hearing. 56: - Cited in note 30, paragraph 33 of the judgment. 57: - Paragraph 61. 58: - Sixth, seventh and eighth indents in Article 6(5). 59: - Cited in note 31, paragraph 71 of the judgment. 60: - This appears to be feasible, since the first indent of Article 6(5) of the Regulation requires the consignment note to include information concerning the source, composition and quantity of the waste for recovery ... and, in the case of waste from various sources, a detailed inventory of the waste. 61: - Directive of 12 December 1991, OJ 1991 L 377, p. 20. 62: - Set out in paragraph 6 above. 63: - See paragraph 6 above. 64: - Council Directive 89/369/EEC of 8 June 1989 on the prevention of air pollution from new municipal waste incineration plants, OJ 1989 L 163, p. 32. 65: - Council Directive 89/429/EEC of 21 June 1989 on the reduction of air pollution from existing municipal waste-incineration plants, OJ 1989 L 203, p. 50. 66: - Directive 2000/76/EC of the European Parliament and of the Council of 4 December 2000 on the incineration of waste, OJ 2000 L 332, p. 91. 67: - See for example Case C-5/94 Hedley Lomas [1996] ECR I-2553, paragraph 20 of the judgment and the cases there cited. 68: - Final recital in the preamble to each directive. 69: - Case C-324/99 DaimlerChrysler [2001] ECR I-9897, paragraphs 48 to 65 of the judgment. 70: - Cited in note 31, paragraph 68 of the judgment.