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Súdny dvor Európskej únie·4.10.2001

C-161/00

ECLI:EU:C:2001:515

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Súdny dvor Európskej únie
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62000CC0161

COMMISSION v GERMANY

OPINION OF ADVOCATE GENERAL GEELHOED delivered on 4 October 2001 1

I — Introduction caused or induced by nitrates from agricul- tural sources and preventing further such pollution. 1. The central question in these infringe- ment proceedings is whether it is permis- sible, in the implementation of Council Directive 91/676/EEC of 12 December 3. Article 2(h) provides that 'land applica- 1991 concerning the protection of waters tion' means 'the addition of materials to against pollution caused by nitrates from land whether by spreading on the surface of agricultural sources 2 (hereinafter 'the the land, injection into the land, placing Directive'), to take the nitrogen losses below the surface of the land or mixing resulting from the storage and spreading with the surface layers of the land'. of livestock manure into account in the calculation of the maximum amount of such manure which may be applied to the 4. Under Article 5(1), Member States are land per hectare each year. This question, required, for the purpose of realising the which is of a technical nature, is not objectives specified in Article 1, to establish without importance. The losses which action programmes in respect of vulnerable may be taken into account in the Federal zones. In accordance with Article 5(4) of Republic of Germany are 10 to 25% of the the Directive, the action programmes are to total amount of nitrogen. be implemented within four years of their establishment. They must consist of

'(a) the measures in Annex III'; I I — Legal framework

and A — The 'Nitrates Directive'

'(b) those measures which Member States have prescribed in the code(s) of good agricultural practice established in accord- 2. Under Article 1, the Directive has the ance with Article 4...'. objective of reducing water pollution

1 — Original language: Dutch. 5. Annex III provides in point 1 that the 2 — OJ 1991 L 375, p. 1. measures to be included in action pro-

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grammes as referred to in Article 5(4) must (i) the foreseeable nitrogen require- include the following rules: ments of the crops,

'... and

(ii) the nitrogen supply to the crops 3. limitation of the land application of from the soil and from fertilisation fertilisers, consistent with good agri- corresponding to: cultural practice and taking into account the characteristics of the vul- nerable zone concerned, in particular:

— the amount of nitrogen present in the soil at the moment when the crop starts to use it to a (a) soil conditions, soil type and slope; significant degree (outstanding amounts at the end of winter),

(b) climatic conditions, rainfall and — the supply of nitrogen through irrigation; the net mineralisation of the reserves of organic nitrogen in the soil,

(c) land use and agricultural practices, including crop rotation systems; and to be based on a balance — additions of nitrogen com- between: pounds from livestock manure, I - 2756

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— additions of nitrogen com- to prejudice the achievement of the pounds from chemical and objectives specified in Article 1 other fertilisers.' and must be justified on the basis of objective criteria, for example:

6. Point 2 in Annex III is worded as follows: — long growing seasons;

'2. These measures will ensure that, for each farm or livestock unit, the amount of livestock manure applied to the land — crops with high nitrogen each year, including by the animals uptake; themselves, shall not exceed a specified amount per hectare.

The specified amount per hectare shall — high net precipitation in the be the amount of manure containing vulnerable zone; 170 kg N. However:

(a) for the first four-year action pro- — soils with exceptionally high gramme Member States may allow denitrification capacity. an amount of manure containing up to 210 kg N;

If a Member State allows a different (b) during and after the first four-year amount under subparagraph (b), it action programme, Member States shall inform the Commission which may fix different amounts from will examine the justification in those referred to above. These accordance with the procedure laid amounts must be fixed so as not down in Article 9.'

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B — The relevant German legislation spreading', up to a maximum of 20% of the total amount of nitrogen calculated before spreading.

7. The Verordnung über die Grundsätze der guten fachlichen Praxis beim Düngen 3 (Regulation on the principles of good 10. Under Paragraph 4(5) of the Düng- manuring and fertilising practice; here- everordnung, the total nitrogen content of inafter 'the Düngeverordnung') of 26 Janu- farmyard livestock manure applied to the ary 1996 is, in part, intended to implement land must be determined on the basis of the Nitrates Directive in Germany. analyses or by applying specific recognised methods of calculation and estimation or reference values. In the latter case, the final sentence of Paragraph 4(5) provides that in the case of liquid manure and slurry 10% and in the case of solid manure 25% of the total amount of nitrogen contained in the livestock excreta may be deducted 'as storage losses' if those amounts are not 8. Paragraph 3 of the Düngeverordnung taken into account in the particular contains some principles specific to farm- methods of calculation and estimation or yard livestock manure. Paragraph 3(7) reference values adopted. provides that, without prejudice to the principles in Paragraphs 2, 3(1) to (6) and 4, the quantity of livestock manure to be applied per farm per year may not exceed the following total amounts of nitrogen: 210 kg for pasture land; 210 kg (until 30 June 1997) and 170 kg (from 1 July 1997 onwards) for arable land. I I I — Procedure

11. On 15 May 1995, the Commission sent 9. Under the final sentence of Paragraph the Federal Republic of Germany a letter of 2(1) of the Düngeverordnung, account may formal notice raising a number of issues be taken, when applying farmyard livestock concerning the implementation of the manure to the land, of the nitrogen losses Directive in Germany. On 11 July 1997 resulting from 'the inevitable losses during the Commission sent a further letter of formal notice. The reasoned opinion, which was sent on 29 September 1998, concen- 3 —BGBl. 1996 1, p. 118. trated on the alleged failure to comply with

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the obligations under Article 5(4)(b) of, 4 The Federal Republic of Germany claims and points 1(2) and 2 in Annex III to, the that the action should be dismissed and the Directive. On the basis of the information Commission ordered to pay the costs. provided by the German Government, the Commission decided to confine its criticism from then on solely to the Düngeverord- nung, which, in its view, was not in accordance with the requirements of Article 5(4)(a) of, and point 2 in Annex III 13. In these proceedings, the President of to, the Directive. The application in the the Court has granted the Kingdom of present case was lodged at the Court Spain and the Kingdom of the Netherlands Registry on 28 April 2000. leave to intervene in support of the Federal Republic of Germany.

12. The applicant claims that the Court should: IV — Pleas in law and main arguments

14. The Commission is of the opinion that the German rules, as laid down in the Düngeverordnung, are likely to cause the (1) declare that the Federal Republic of application of manure to the land in Germany has failed to fulfil its obli- quantities exceeding the maximum quan- gations under Article 5(4)(a) of, and tity of fertilisers which any one arable and point 2 in Annex III to, Council Direc- livestock farm is allowed to apply per tive 91/676/EEC of 12 December 1991 hectare and per year. The provisions in concerning the protection of waters question are therefore not in accordance against pollution caused by nitrates with Article 5(4)(a) of, and points 1(3) and from agricultural sources; 2 in the Annex to, the directive.

15. The Commission points out that the action p r o g r a m m e s referred to in (2) order the Federal Republic of Germany Article 5(4) must include the measures to pay the costs. described in Annex III. In accordance with points 1(3) and 2 of that annex, those measures are to include rules concerning 4 — It is clear from the context of the reasoned opinion that this was a drafting error. The Commission must have intended the 'limitation of the land application of to invoke Article 5(4)(a) of the Directive. The latter fertilisers', which must ensure that, 'for provision does in fact refer to the measures in Annex III to the Directive. each farm or livestock unit, the amount of

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livestock manure applied to the land each nitrogen is regarded as a 'normal' loss year, including by the animals themselves, arising from volatilisation of the nitrogen. shall not exceed a specified amount per hectare'. That specified amount per hectare is to be the amount of manure containing 170 kg N (nitrogen), although for the first four-year action programme Member 18. However, according to the Commis- States may allow an amount of manure sion, that disregards the fact that a large containing up to 210 kg N, and even proportion of the amounts of nitrogen thereafter, under point (b) of the second which escape into the air eventually fall subparagraph of point 2 in Annex III to the back onto the land and into watercourses, directive, derogations based on objective thereby contributing to water pollution. grounds are possible. However, the purpose of the Directive is to combat water pollution, by which the Directive understands the discharge, both directly and indirectly, of nitrogen com- pounds from agricultural sources.

16. However, the effect of the German rules in question is that more than 170 and/or 210 kg of nitrogen may end up on 19. The Commission further argues that the land and therefore in waters. the Directive fixes in absolute terms the maximum permitted amount of nitrogen which may be applied to the land, without any provision for the possibility of deduc- tions. The Directive does not contain any legal basis for taking into account losses arising during the land application process.

17. Under Article 2(h) of the Directive, 'land application' means 'the addition of materials to land whether by spreading on the surface of the land, injection into the 20. In the Commission's opinion, the land, placing below the surface of the land Directive makes no distinction between or mixing with the surface layers of the the start and end of the 'land application' land'. However, the German statutory process. According to it, the decisive cri- provisions contained in the Düngeverord- terion, which can be inferred from the nung, namely the final sentence of Para- wording and purpose of the Directive, is graph 2(1) and in Paragraph 4(5), allow the amount of nitrogen which is added to account to be taken, within specified limits, the land by spreading on the surface of the of 'unavoidable losses during spreading on land, injection into the land, placing below the land' in the case of farmyard livestock the surface of the land or mixing with the manure or 'storage losses' in the case of surface layers of the land. The Directive liquid manure, slurry and solid dung. The does not refer to the amount which is effect of the possibility of deduction is that actually absorbed into the soil, but to the a certain percentage of the total amount of amount which lands on the soil.

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21. The Commission acknowledges that is to say, on or in the ground, which the different language versions of point 2 matters. That interpretation accords with in Annex III to the Directive are not com- the purpose of the provision. pletely identical. The German version uses the term 'die auf den Boden ausgebrachte Dungmenge' ('the amount of livestock manure applied to the land'). That is, to some extent, a pleonasm, since Article 2(h) 23. The German Government, supported in defines 'Ausbringen' ('land application') as this by the intervening Member States, 'Aufbringen auf den Boden...' ('addition of counters the Commission's view with a materials to land'). The term 'auf den number of arguments based on the word- Boden' is therefore expressed twice. The ing, purpose and scheme of the Directive. same thing occurs in the English version The taking into account of nitrogen losses where point 2 in Annex III has 'manure is in accordance with the Directive and the applied to the land' and the definition in Commission also gave the impression of Article 2(h) is worded: '"land application": allowing it. the addition of materials to land...'. The French-language version speaks in Annex III of 'quantité d'effluents d'élevage épan- due' and Article 2(h) refers to '"épandage": l'apport au sol de matières...'. The Italian wordings are, respectively, 'quantitativo di V — Assessment effluente di allevamento sparso sul terreno' and 'per "applicazione al terreno": si intende l'apporto di materiale al terreno'; in the Spanish version, those wordings are 'la cantidad de estiércol aplicada a la tierra' 24. The answer to the question of law and '"aplicación sobre el terreno": la raised in this case — whether inevitable incorporación de sustancias al mismo'. losses may be taken into account in calcu- lating the maximum allowable amount of nitrogen — is in essence dependent on the answer to another question, namely, at what moment the calculation of the maxi- mum permitted amount of 170 or 210 kg of nitrogen must take place. The issue is whether, as the Commission believes, the decisive moment is when the nitrogen is present in the fertiliser, or whether, as the Federal Republic of Germany and the intervening Member States argue, it is 22. A comparison of those different lan- when the nitrogen actually enters the soil. guage versions leads the Commission to It is common ground that the Member conclude that, despite the differences exist- States are not entitled to decide at their ing between them, and even the incon- own discretion on the method of calculat- sistency which appears within one language ing the limit value. The method and version, the moment of land application moment of measurement must be deter- must, as a rule, be decisive for the purposes mined objectively and in a consistent and of the calculation. It is not the moment identical manner throughout the Commu- when the nitrogen is on or in the land, that nity.

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25. In my view, the Commission has shown 28. Since the wording of point 2 in Annex satisfactorily that, in the light of the word- III is not clear, the provision must be ing, objectives and context of the Directive, interpreted in the light of the objectives the decisive moment for the calculation of and context of the Directive. 5 the maximum permitted amount of nitrogen is when the fertiliser — and thus the nitrogen — is actually applied, and not the moment when the nitrogen is on the land or even in the soil, that to say, below the surface of the land. 29. In the Community, nitrates from agri- cultural sources are the main cause of water pollution from diffuse sources. The Direc- tive, which is based on Article 130s of the 26. The Directive gives few explicit indi- EC Treaty (now, after amendment, cations as to how the Member States are to Article 175 EC), is therefore intended to determine the maximum permitted amount reduce or prevent water pollution caused or of nitrogen on the basis of 'the amount of induced by those sources. The purpose of livestock manure applied to the land' that is to protect human health and living within the meaning of point 2 in Annex III. resources and aquatic ecosystems and to 'Land application' is defined in Article 2(h) safeguard other legitimate uses of water. 6 of the Directive as 'the addition of materials to land whether by spreading on the surface of the land, injection into the land, placing below the surface of the land or mixing with the surface layers of the land'. An examination of the different language versions, to which the Commis- sion refers, does not give a clear picture. 30. For the purpose of identifying waters affected by pollution, the Directive refers to the limit value of 50 milligrams per litre laid down in Directive 75/440/EEC. 7The measurement of water pollution caused by 27. The German Government argued dur- nitrates from agricultural sources is dif- ing the procedure that, because of the use ficult and dependent on various factors. of the past tense in the phrase 'amount... The degree to which groundwater pollution applied' in point 2 in Annex III, account occurs is connected, for example, with the could also be taken, for the purpose of the soil structure, the crops grown, and the calculation, of the emission losses which season in which the measurement is carried took place before the nitrogen actually settled on the ground. However, I share 5 — Settled case-law; see recently Case C-191/99 Kvaerner the Commission's view that the Directive in [2001] ECR I-4447, paragraph 30. no way makes a distinction between the 6 — See the fifth and sixth recitals in the preamble to the start and the end of the land application Directive. 7 — Council Directive of 16 June 1975 concerning the quality process. The precise moment of addition is required of surface water intended for the abstraction of drinking water in the Member States (OJ 1975 L 194, not stated. It may be when the fertiliser is p. 26). That directive was replaced by Directive 2000/60/EC injected into the ground, but it may also be of the European Parliament and of the Council of 23 Oc- tober 2000 establishing a framework for Community action before that. in the field of water policy (OJ 2000 L 327, p. 1).

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out. Thus, dry sandy and loessial soils are that, for each farm or livestock unit, the more prone to erosion than clay and peat amount of livestock manure applied to the soils, different crops do not have the same land each year does not exceed a limit value nitrate uptake, pollution in seasons with of 170 kg of nitrogen per hectare. Under precipitation is greater than in dry seasons, point 2(a) in Annex III, for the first four- and the amount of nitrogen produced by year action programme they may allow an dairy cows is significantly greater than that amount of manure containing up to 210 kg produced by pigs reared for meat. of nitrogen.

31. The Directive therefore does not seek to harmonise the relevant national laws, but to create the instruments needed in 33. The Netherlands, German and Spanish order to ensure that waters in the Commu- Governments suggested that there are three nity are protected against pollution caused factors connected with the scheme of the by nitrates from agricultural sources. 8 directive which would justify allowing Those instruments consist in the adoption different amounts or else taking into of codes of good agricultural practice account nitrogen losses in the calculation applicable to all waters susceptible to of the maximum amount. However, I am pollution, and in the implementation of not persuaded by the arguments put for- action programmes which include measures ward. for vulnerable zones. The nature of the Directive means that the Member States may apply it differently in a number of respects. 9

34. In its statement in intervention, the 32. On one point, however, the Directive N e t h e r l a n d s G o v e r n m e n t invokes does not leave the Member States any point 2(b) in Annex III to the Directive. discretion whatsoever. In respect of pollu- Under that provision, different amounts are tion by nitrates from livestock manure, the allowed, provided that the achievement of Directive lays down an unequivocal and the objectives specified in Article 1 is not absolute limit value. Point 2 in Annex III prejudiced and that such amounts are clearly states that the measures to be justified on the basis of objective criteria, adopted by the Member States must ensure such as long growing seasons, crops with high nitrogen uptake, high net precipitation in the vulnerable zone, and soils with 8 — See Case C-293/97 Standley and Others [1999] ECR I-2603, exceptionally high denitrification capacity. paragraph 39. However, it is beyond dispute that the 9 — Standley and Others, cited in footnote 8, paragraphs 37 to 39. generally applicable deduction rule in the

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Düngeverordnung does not satisfy those can be determined only if losses through objective criteria. Moreover, a Member ammonia volatilisation — as well as State which allows a different amount must nitrogen uptake as a consequence of pre- inform the Commission. During the pro- cipitation — are taken into account in cedure it did not appear, with regard to calculating the balance. Paragraph 2(1), final sentence, and Para- graph 4(5), of the Düngeverordnung, that the Federal Republic of Germany had complied with the obligation to inform contained in the final sentence of point 2(b) in Annex III. 37. Pursuant to Paragraph 4(1)(2) of the Düngeverordnung, when determining the amount of fertiliser required by crops, nitrogen deposition, which may be deducted beforehand at the time of storage and application (storage and application loss), must be added back on to the required amount of fertiliser. This addition 35. Invoking the balance principle of nitrogen deposition therefore cancels out expressed in point 1(3) in Annex III to the the contested deduction of nitrogen losses Directive, which is also contained in the and ensures that the limit values laid down Düngeverordnung, the German Govern- in the Directive are not in fact exceeded. ment rejects the Commission's argument The German Government is of the opinion that no account is taken of escaped that the aim of the Directive is thus nitrogen which settles back on the land achieved by Paragraph 4(5) and Paragraph and thereby contributes to water pollution. 2(1) of the Düngeverordnung, not so much on their own, but in combination with Paragraph 4(1)(2) of the Düngeverord- nung.

36. According to the German Government, the nitrogen balance is achieved less by the 38. In my opinion, that argument is unten- fact that the nitrogen needed by the plants able both in the light of the scheme of the is present in the fertiliser at any given Directive and on the basis of the Düng- moment than by the fact that the nitrogen everordnung itself. is still actually present in the specified proportion at the time when the fertiliser is applied to the land. The decisive factor is thus the quantity of nitrogen which actually ends up in the soil. Only that quantity can reach the roots of the plants and thus meet the calculated nitrogen requirements. 39. The nitrogen balance system in the According to the German Government, Directive implies that, in determining what the required supply of nitrogen to the crops measures will most effectively combat pol- I - 2764

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lution, account should be taken not only of 41. Second, the Düngeverordnung allows a general local conditions, such as the cli- flat-rate deduction of 10 to 25% regardless matic conditions, but also of the balance of the balance existing in a given area between the nitrogen requirement of the between the nitrogen requirements of and crops and the nitrogen supply to the crops. the nitrogen supply to the crops. As the The nitrogen may either originate in the Commission argues in its reply, that system soil or be supplied by fertilising with live- takes no account at all of the particular stock manure, mineral fertiliser or other circumstances of the individual case. It is fertilisers. The calculation of the balance conceivable that in reality, in a particular assumes that account is taken in a scientific situation, there may be no or only minimal manner of the necessary requirements of loss through volatilisation during appli- the crops and also that the various supply cation or storage, whereas the Düngever- flows of nitrogen are administered as pre- ordnung allows a larger deduction. The cisely as possible. Because certain crops final sentence of Paragraph 2(1)(2) of the have a large nitrogen requirement and the Düngeverordnung contains a flat-rate rule natural addition of nitrogen from the soil whereby 'inevitable losses' relate only to or by deposition is minimal, the balance volatilisation of farmyard manure present calculation may indeed result, in some at the place of storage. No connection with circumstances, in the possibility of more the balance system in Paragraph 4(2) is than 170 or 210 kg of nitrogen per year and established. Under that provision, account per hectare being applied to the land. may thus be taken of losses even where they are not justified on the basis of the actual nitrogen balance. The same applies with regard to slurry, liquid manure and solid farmyard manure within the meaning of Paragraph 4(5) of the Düngeverordnung. That provision allows account to be taken of a loss of 10 to 25% if that quantity is not taken into account in the recognised calcu- lation and estimation methods or reference values. There is no mention of any con- nection with the nitrogen balance. 40. However, that is not sufficient to justify the deduction system in the Düng- everordnung. First, point 2 in Annex III to the Directive prohibits the supply of live- stock manure from exceeding the maxi- mum amount of 170 or 210 kg of nitrogen, however great the extra requirement for nitrogen compounds from fertilisers may be. The requirements which the measures included in action programmes as referred to in Article 5(4)(a) of the Directive must 42. The Spanish Government draws atten- satisfy pursuant to point 1 in Annex III tion to the provision concerning the must in any case ensure that the livestock nitrogen balance in the final indent of manure applied each year to the land does point 1(3)(c)(ii) in Annex III. That balance not exceed the amounts mentioned in may take account of the nitrogen supply point 2 in Annex III. corresponding to additions of nitrogen

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compounds from chemical and other ferti- any circumstances. If the Community legis- lisers. According to the Spanish Govern- lature had intended account to be taken of ment, such 'other fertilisers' might include nitrogen losses in the calculation of the the ammonia which, generally speaking, is maximum amount of livestock manure discharged via the atmosphere by, for which may be applied per hectare of land example, chemical fertilisers, municipal each year, that intention would have had to waste and municipal waste water. It argues be expressly stated in the directive. Since that disposal into the atmosphere should be that is not the case, a Member State may regulated in a comprehensive framework. not unilaterally increase the maximum From a technical point of view, there does values. Consequently, when the maximum not seem to be any justification for regulat- amount is calculated, due allowance must ing only the atmospheric deposition of be made for storage loss in the case of livestock manure. farmyard manure and inevitable losses arising during spreading in the case of slurry and liquid manure. Those losses may not be added to the maximum permissible amounts of 170 or 210 kg, but must form part thereof.

43. It is true that under that provision the Member States must take account of all fertilisers when adopting measures con- cerning the nitrogen balance. However, as the Commission rightly observes, that fact is not relevant when assessing the limit values in point 2 in Annex III to the 45. That conclusion is reinforced by a Directive. The latter provision is in fact number of further arguments. concerned exclusively with livestock manure, that is to say, with animal excreta, and not with other possible fertilisers which also contain nitrates and pollute water.

46. First, that interpretation is supported by the definition of the term 'pollution' in Article 2(j) of the Directive. It means not only direct discharge of nitrogen com- 44. In my view, the Commission was there- pounds from agricultural sources into the fore right to challenge the German provi- aquatic environment, but also indirect dis- sions. The Düngeverordnung does not charge. Indirect discharge may take place if exclude an increase in the maximum per- the amounts of nitrogen which have missible amounts of nitrogen mentioned in escaped through volatilisation return onto point 2 in Annex III. The German Govern- or into the soil. The interpretation in ment has failed to show that there can be question is the one most consistent with no question of the maximum permissible the purpose of the Directive, which is to amount of 170 or 210 kg being exceeded in reduce water pollution. I - 2766

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47. Moreover, it is not clear why the to be more careful in their handling of the Düngeverordnung assumes losses of 10 to nitrogen losses resulting from the storage 25%. The German Government claims that and spreading of manure. The margin those flat-rate values are based on scientific allowed by the Düngeverordnung is in fact data, but there is no concrete evidence to technically unlimited. As a result, the support those maximum percentages. If national environment may be more heavily Member States are free to fix percentages polluted than is strictly necessary, which which may be taken into account when also undermines the practical effectiveness calculating the maximum amount of of the Directive. nitrogen, uncertainty may develop with regard to only absolute limit value con- tained in the Directive, thereby undermin- ing the practical effectiveness of the Direc- tive.

50. Furthermore, an interpretation such as that advocated by the German Government is not in line with the tendency nowadays not to combat negative environmental effects in isolation, but in a comprehensive and integrated manner. Under point 2 in Annex III to the Directive, the limit value 48. The risk of divergent percentages must be calculated per hectare and on an appearing is even greater if each Member annual basis 'for each farm or livestock State determines as it sees fit the loss unit'. The best system would therefore be coefficients which may be taken into to base that calculation on the fertiliser account. The German Government's obser- cycle within a farm. Other loss factors vation that other Member States also take which arise up to the time of land appli- account of losses through volatilisation and cation, such as losses in the stables and that the values in the Düngeverordnung are during spreading, will then be covered. The not excessive in comparison with the rules fact that the Directive takes no account of in other Member States is clearly not a the nitrogen losses after the land appli- sufficient argument for retaining the deduc- cation of the fertiliser does not prevent tion system in the Düngeverordnung. If that. other Member States exceed the maximum nitrogen values permitted by the Directive, that cannot in any circumstances justify an infringement of the provisions of the Direc- tive by the Federal Republic of Germany.

51. Moreover, a strict interpretation is in keeping with the principle enshrined in the Treaty that pollution should be rectified as close as possible to the source. 10 In this case, that means that the rectification of

49. Moreover, the unilateral fixing of a flat-rate margin does not encourage farms 10 —See Article 174(2) EC.

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water pollution by nitrates must be com- 2000. The only issue discussed during that menced at as early a stage as possible. The meeting was that of nitrogen losses and calculation of the maximum permissible possible solutions for their calculation. amount of livestock manure as from the Even apart from that, the Commission has place of storage, instead of at the time of rightly pointed out that its departments' land application, contributes — even if contributions to the discussions within the indirectly — to the achievement of that committee could not be regarded as defini- objective. tive statements of what the Commission considers permissible under Community law. The Commission is obviously not bound in law by the solutions which it suggests within the committee.

52. It remains for me to examine the Commission's approach, which has been criticised on two points. First, the German and Spanish Governments point out that the Commission's position in these pro- ceedings does not accord with the view expressed by the Commission represen- tative during a meeting, held on 11 April 2000, of the Nitrates Committee estab- lished pursuant to the Directive. At that meeting, the Commission had indicated, on 54. The same applies mutatis mutandis the basis of a presentation and a working with regard to the German Government's document, that it was preparing a proposal argument that it can be inferred from a for harmonising the calculation of nitrogen letter of 3 December 1997 from the Com- losses. At the same time, the Nitrates mission's Environment Directorate-General Committee had come to the conclusion at to the Permanent Representation of the that meeting that ammonia discharges from Federal Republic of Germany that the livestock manure which is not actually Commission approved of the provisions applied to the land do not have to be taken concerning losses in the Düngeverordnung. into account in the calculation of the limit That letter contains a response to a debate values laid down in point 2 of Annex III about the interpretation of point 2 in either. Annex III at a meeting of the Nitrates Committee held on 12 June 1997. The Commission can in no way be bound by that letter in these proceedings. That would not be of much help to the Federal Republic of Germany in any case. It should be observed for the record that the letter relates primarily to the losses which arise 53. However, as the German Government after the land application of the manure, had to admit in the rejoinder, no official whereas the Commission confirms in its Commission position concerning a pro- letter that the amounts specified in the posal for harmonisation was put forward directive are to be understood as amounts at the abovementioned meeting of 11 April 'as from the place of storage'.

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VI — Conclusion

55. In the light of the foregoing, I propose that the Court:

(a) declare that the Federal Republic of Germany has failed to fulfil its obligations under Article 5(4)(a) of, and point 2 in Annex III to, Council Directive 91/676/EEC of 12 December 1991 concerning the protection of waters against pollution caused by nitrates from agricultural sources;

(b) order the Federal Republic of Germany to pay the costs pursuant to Article 69(2) of the Rules of Procedure;

(c) declare that the Kingdom of Spain and the Kingdom of the Netherlands are to bear their own costs pursuant to Article 69(4) of the Rules of Procedure.

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