2002/399/EC: Commission Decision of 24 May 2002 on the national provisions notified by the Kingdom of Sweden under Article 95(4) of the EC Treaty concerning the maximum admissible content of cadmium in fertilisers (Text with EEA relevance) (notified under document number C(2002) 1932)
Date: 2002-05-24
Institutions: European Commission
Subjects: Sweden, cadmium, derogation from EU law, fertiliser, national law

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COMMISSION DECISION

of 24 May 2002

on the national provisions notified by the Kingdom of Sweden under Article 95(4) of the EC
Treaty concerning the maximum admissible content of cadmium in fertilisers

(notified under document number C(2002) 1932)

(Only the Swedish text is authentic)

(Text with EEA relevance)

(2002/399/EC)

THE COMMISSION OF THE EUROPEAN COMMUNITIES,

Having regard to the Treaty establishing the European Community, in particular Article 95(6) thereof,

Whereas:

I. FACTS

1. COMMUNITY LEGISLATION

(1)

(2)

Council Directive 76/116/EEC of 18 December 1975 on the approximation of the laws of the
Member States relating to fertilisers (1), as last amended by Directive 98/97/EC (2), lays down the
requirements that fertilisers must fulfil in order to be placed on the market with the designation ‘EC
fertilisers’ (3).

Annex I of the Directive 76/116/EEC sets out the type designation and the corresponding require-
ments, e.g. with respect to its composition, that each EC-designated fertiliser must fulfil. EC-desig-
nated fertilisers included in this list are grouped into categories, depending on the content of the
primary nutrients,

i.e. the elements nitrogen, phosphorus and potassium.

(3)

Directive 76/116/EEC has been amended and adapted to technical progress several times in order,
inter alia, to include new fertiliser-types in Annex I.

(4)

The amendments to Directive 76/116/EEC have been introduced by the following Directives:

— Directive 88/183/EEC (4) has extended the scope of Directive 76/116/EEC to include in Annex I

straight and compound fluids fertilisers,

— Directive 89/284/EEC (5) has extended the scope of Directive 76/116/EEC to include in Annex I

fertilisers containing calcium, magnesium, sodium and sulphur,

— Directive 89/530/EEC (6) has extended the scope of Directive 76/116/EEC to include in Annex I

solid or liquid fertilisers containing:

— one of the following trace elements: boron, cobalt, copper, iron, manganese, molybdenum

and zinc,

— mixtures of such fertilisers containing at least two of these trace elements,

— a list of authorised organic chelating agents for trace elements.

(1) OJ L 24, 30.1.1976, p. 21.
(2) OJ L 18, 23.1.1999, p. 60.
(3) The term ‘EEC fertilizer’ provided for by Directive 76/116/EEC was replaced by the term ‘EC fertiliser’ by Directive

97/63/EC (OJ L 335, 6.12.1997, p. 15)

(4) OJ L 83, 29.3.1988, p. 33.
(5) OJ L 111, 22.4.1989, p. 34.
(6) OJ L 281, 30.9.1989, p. 116.

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(5)

(6)

(7)

(8)

(9)

The adaptations to technical progress to Directive 76/116/EEC have been introduced by Directive
93/69/EEC (7), Directive 96/28/EC (8) and Directive 98/3/EC (9). Under these Directives, new fertilisers
are added to the Annexes of Directive 76/116/EEC.

For the purposes of this Decision, the term Directive 76/116/EEC shall be construed as referring to
that Directive as amended by the Directives mentioned in recitals 4 and 5 above.

The rules governing the composition of fertilisers covered by Directive 76/116/EEC do not provide
for a limit value for the cadmium content of EC-designated fertilisers.

According to Article 7 of Directive 76/116/EEC, Member States may not on grounds of composition,
identification, labelling or packaging, prohibit, restrict or hinder the marketing of fertilisers marked
‘EC fertiliser’ which comply with the provisions of this Directive and the Annexes thereto.

2. THE ACCESSION OF SWEDEN

Sweden acceded to the European Union on 1 January 1995. The Act of Accession (10) lays down
transitional provisions concerning the use and marketing of cadmium in that State. Article 112(1)
provides that during a period of four years from the date of accession, the provisions referred to in
Annex XII of the Act shall, in accordance with that Annex and subject to the conditions set out
therein, not apply to Sweden. Article 112 and point 4 of Annex XII of the Act of Accession provide
that Article 7 of Directive 76/116/EEC, in so far as it concerns the cadmium content of fertilisers,
shall not apply to Sweden before 1 January 1999 and that the provisions of Directive 76/116/EEC
will be reviewed in accordance with Community procedures by 31 December 1998.

(10) Article 2 of the Act of Accession provides that ‘from the date of accession, the provisions of the
original Treaties and the acts adopted by the institutions before accession shall be binding on the
new Member States and shall apply in those States under the conditions laid down in those Treaties
and in this Act’. Article 168 of the Act of Accession stipulates that ‘the new Member States shall put
into effect the measures necessary for them to comply, from the date of accession, with the
provisions of directives and decisions within the meaning of Article 189 (now Article 249) of the EC
Treaty […], unless a time limit is provided for in the list of Annex XIX or in any other provisions of
this Act’.

(11) Directive 98/97/EC of the European Parliament and of the Council (11) subsequently amended
Directive 76/116/EEC as regards the marketing in Austria, Finland and Sweden of
fertilisers
containing cadmium. Article 1 provides that, inter alia, Sweden may prohibit the marketing on its
territory of fertilisers containing cadmium at concentrations in excess of that which was fixed
nationally at the date of accession and that this derogation applies for the period from 1 January
1999 until 31 December 2001.

3. NATIONAL PROVISIONS

(12)

(13)

‘The Chemicals Products (Handling, Import and Export Prohibitions) Ordinance’
(1998:944) (12)
contains provisions relating, inter alia, to the maximum permissible cadmium content in fertilisers,
including EC-designated fertilisers. Section 3, paragraph 3, of the Ordinance, provides that fertilisers
covered by customs tariffs numbers 25.10, 28.09, 28.35, 31.03 and 31.05 containing in excess of
100 grams of cadmium per tonne of phosphorous may not be offered for sale or transferred.

The provisions relating to the maximum permissible cadmium content in fertilisers have been in
force since 1985 following the adoption of ‘The Cadmium Ordinance’ (1985:839). ‘The Chemicals
Products Ordinance’
(1998:944) codifies different provisions relating to the protection of the
environment,

including those contained in ‘The Cadmium Ordinance’ (1985:839).

(7) OJ L 185, 28.7.1993, p. 30.
(8) OJ L 140, 13.6.1996, p. 30.
(9) OJ L 18, 23.1.1998, p. 25.
(10) OJ C 241, 29.8.1994, p. 41 and p. 316.
(11) OJ L 18, 23.1.1999, p. 60.
(12) Swedish Code of Statutes (SFS Svensk Författningssamling) of 14 July 1998.

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II. PROCEDURE

(14)

(15)

(16)

By letter of 7 December 2001, the Swedish authorities notified the Commission that Sweden, in
accordance with article 95(4) of the EC Treaty, intends to continue to apply from 1 January 2002
national provisions concerning the cadmium content in fertilisers.

By letter of 8 January 2002, the Commission informed the Swedish authorities that it had received
the notification under Article 95(4) and that the six months period for its examination according to
Article 95(6) started on 8 December 2001, the day following the one when the notification was
received.

By letter of 23 January 2002, the Commission informed the other Member States about the request
received from Sweden. The Commission also published a notice regarding the request in the Official
Journal of the European Communities (13) in order to inform other interested parties of the national
measures that Sweden intends to maintain.

III. ASSESSMENT

1. CONSIDERATION OF ADMISSIBILITY

(17) Article 95(4) of the Treaty provides that, if, after the adoption by the Council or by the Commission
of a harmonisation measure, a Member State deems it necessary to maintain national provisions on
grounds of major needs referred to in Article 30, or relating to the protection of the environment or
the working environment, it shall notify the Commission of these provisions as well as the grounds
for maintaining them.

(18)

The notification submitted by the Swedish authorities on 7 December 2001 intends to obtain
authorisation to maintain national provisions incompatible with those concerning the composition
of EC-denominated fertilisers contained in Directive 76/116/EEC.

(19) As already indicated, Article 7 of Directive 76/116/EEC prevents Member States from restricting the
marketing of EC-denominated fertilisers because of their composition, but the rules governing
composition do not set any limit value for cadmium content. This means that pursuant to Article 7
of Directive 76/116/EEC, EC-denominated fertilisers complying with the requirements of
that
Directive can be placed on the market regardless of their cadmium content.

(20)

(21)

In the light of the abovementioned, it is clear that the national provisions notified by Sweden, in so
far as they prohibit the placing on the market of phosphorus-based EC-denominated fertilisers with a
cadmium content exceeding 100 grams per tonne of phosphorus, are more restrictive than those
contained in Directive 76/116/EEC.

The national provisions notified by the Swedish authorities were adopted in 1985, therefore before
Sweden acceded to the European Union. As indicated above, the Act of Accession lays down
transitional provisions allowing Sweden to continue to apply its national provisions concerning the
cadmium content of fertilisers to products covered by Directive 76/116/EEC for a period of four
years. By Directive 98/97/EC, Sweden was authorised to continue to apply the above national
provisions until 31 December 2001.

(22) As required by Article 95(4), as interpreted in the light of Articles 2 and 168 of the Act of Accession,
Sweden notified the Commission of the actual wording of the provisions adopted before the
accession to the European Union that it intends to maintain, accompanying the request by an
explanation of the reasons which,

justify the maintenance of those provisions.

in its opinion,

(13) OJ C 23, 25.1.2002, p. 6.

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(23)

The notification submitted by Sweden on 7 December 2001 in order to obtain approval for
maintaining national provisions derogating from the provisions of Directive 76/116/EEC, is therefore
to be considered admissible under Article 95(4) as interpreted in the light of Articles 2 and 168 of
the Act of Accession.

2. ASSESSMENT OF MERITS

(24)

(25)

(26)

(27)

In accordance with Article 95 of the Treaty, the Commission has to ensure that all the conditions
enabling a Member State to avail itself of the possibilities of derogation provided for in this article
are fulfilled.

In particular, the Commission has to assess whether the provisions notified by the Member State are
justified on grounds of major needs referred to in Article 30 of the Treaty, or relating to the
protection of the environment or the working environment.

In addition, pursuant to Article 95(6) of the Treaty, where it considers that the national provisions
are justified, the Commission must check whether or not those national provisions are a means of
arbitrary discrimination or a disguised restriction on trade between Member States and whether or
not they constitute an obstacle to the functioning of the internal market.

Sweden has based its request on the need of protection of human health and the environment.
Cadmium in fertilisers is deemed to pose a threat to the environment and human health. In support
of its request, Sweden makes reference to the conclusions of a Swedish study published on 4
October 2000 (14), which contains an assessment of the environmental risks posed by cadmium-
containing fertilisers.

2.1. JUSTIFICATION ON GROUNDS OF MAJOR NEEDS

2.1.1. General information on cadmium

(28)

Cadmium is a heavy metal naturally present in the environment, but most emissions of this metal
are due to various human activities (production of non-ferrous metals, incineration of fossil fuels,
application of fertiliser, etc.).

(29) A general risk assessment on cadmium metal and cadmium oxide is currently being carried out
under Council Regulation 793/93/EEC of 23 March 1993 on the evaluation and control of the risks
of existing substances (15) with Belgium acting as rapporteur. This risk assessment will address all
important uses and emissions of cadmium. At present only an incomplete draft report is available for
discussions at the technical

level.

(30)

(31)

(32)

From the scientific data available up to now, it can be concluded that cadmium metal and cadmium
oxide in general can be considered to pose serious risks to health. In particular, cadmium oxide has
been classified as a carcinogen, mutagen or substance toxic for reproduction, category 2 (16). It is also
generally agreed that cadmium in fertilisers is by far the most important source of cadmium input to
soil and to the food chain.

2.1.2. Cadmium in fertilisers

Cadmium is present in the natural state in the phosphate mineral rocks which are mined for use as
raw material to manufacture phosphatic mineral fertilisers. In the finished state, these fertilisers
always contain certain amounts of cadmium, depending on the original content of the phosphate
rocks.

Cadmium is regarded as harmful both to the environment and to human health. Phosphate fertilisers
have been identified as a major source of cadmium on arable land, where it tends to accumulate over
time. Crops tend to absorb cadmium from the soil, and the cadmium content of food, which is the
main source of human intake of cadmium, has become an issue of concern for human health. When
ingested in food, cadmium tends to accumulate in the kidneys and may eventually lead to kidney
dysfunction in vulnerable groups.

(14) Swedish National Chemical

Inspectorate, Assessment of risks to health and the environment

in Sweden from

cadmium in fertilisers, 4 October 2000.

(15) OJ L 84, 5.4.1993, p. 1.
(16) See Annex I to Directive 67/548/EEC and Annex I to Directive 76/769/EEC as amended.

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(33)

(34)

The environmental concerns raised by cadmium in fertilisers were first raised at Community level
during the negotiations for the Accession of Austria, Finland and Sweden to the European Union. As
indicated above, those three Member States were granted temporary derogations from Community
legislation on fertilisers in order to allow a careful evaluation of the risks from cadmium in fertilisers
at Community level.

In this context, the Commission first gathered all available data and information on the exposure
situation in the European Community from cadmium in fertilisers. As not enough data were
available in all Member States, the Commission mandated two studies to elaborate a methodology
and procedures with a view to assessing the risks to health and the environment from cadmium in
fertilisers (17). Member States were subsequently invited to carry out nation-wide risk assessments by
making use of the above methodology and procedures.

(35) Nine Member States have completed risk assessments concerning cadmium in fertilisers. These risk
assessments have been made available to the public since September 2001 on the Commission's
web-site (18). In addition, a separate study which analyses these risk assessments has been published
and various options for risk management of cadmium in fertilisers at a Community wide scale have
been developed (19).

(36)

The above risk assessments have also been submitted to the SCTEE (Scientific Committee for
Toxicity, Ecotoxicity and the Environment) and are currently under evaluation. In particular, the
SCTEE has been asked to indicate what is the highest cadmium concentration in fertilisers that can
be tolerated in order to avoid a significant increase in the cadmium content of cultivated soil due to
the application of phosphate fertilisers.

(37)

The completion of the risk assessments took a relatively long time. Moreover, the SCTEE needs time
in order to assess the scientific material thoroughly. It was therefore not possible to present a
proposal for a Regulation on cadmium limits in fertilisers by 31 December 2001.

2.1.3. The risk assessment carried out by Sweden

(38)

The risk assessment submitted by the Swedish authorities is part of the above process of informa-
tion-gathering based on common methodology and procedures. The framework used by Sweden for
conducting its risk assessment is built around three modules:

2.1.3.1. The accumulation module

(39) According to this module, the net accumulation of cadmium in soil and soil solution (or pore
water) (20), resulting from the application of fertiliser, is computed over time and at steady state. The
accumulation module allows for a range of inputs, for example average and extreme rates of
application. The Swedish risk assessment shows that with this module, the following parameters
have been considered:

— the present day cadmium concentration,

— the input of cadmium to agricultural soil through atmospheric deposition, manure and fertiliser

applications,

— the cadmium offtake rate by plants,

— the cadmium leaching rate from the plough layer depending on the cadmium concentration in

the soil pore water and the water flux,

— the concentration of cadmium in the soil and leaching rates at zero and one hundred years.

(17) ERM, Study on data requirements and programme for data production and gathering to support a future evaluation
of the risks to health and the environment from cadmium in fertilisers, March 1999, and A study to establish a
programme of detailed procedures for the assessment of risks to health and the environment from cadmium in
fertilisers, February 2000. (ERM (Environmental Resources Management) is the consultant who developed the metho-
dology for the risk assessments).

(18) http://europa.eu.int/comm/enterprise/chemicals/fertilizers/riskassest/reports.htm
(19) ERM, Analysis and conclusions from Member States' assessment of the risk to health and the environment from

(20) Pore water means that part of the water contained in the soil which is maintained by capillarity between the solid

cadmium in fertilisers, October 2001.

particles of the soil.

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2.1.3.2. The exposure module

(40) According to this module, the uptake of cadmium from soil into cultivated plants and the subse-
quent intake of cadmium by humans are computed, using exposure parameters characterising both
average and extreme exposure scenarios. Environmental exposure is also characterised for vulnerable
environments and is taken to be the predicted cadmium concentration in a particular environmental
compartment.

2.1.3.3. The risk characterisation module

(41)

This module allows Sweden to estimate the incidence and severity of the adverse effects likely to
occur due to actual or predicted exposure to cadmium.

2.1.4. The results of the risk assessment

(42)

The application of the modules has produced the following results:

— concerning surface water, the Swedish risk assessment report states that ‘the chosen PNEC (21)
value implies that in most rivers in southern Sweden, certain biota would already be affected by
cadmium i.e. risk characterisation ratios (22) are larger than one (23). If higher cadmium content in
fertilisers would be allowed, a further increase in the exposure of and the concern for effects in
the aquatic environment is expected to occur’,

— concerning the soil, the Swedish risk assessment report states that ‘by using the Swedish fertiliser
for one hundred years on common Swedish soils (PNEC 0,25 mg/kg), no concern for ecological
effects is predicted when potatoes or wheat are grown. A concern is predicted when carrots are
grown, but this concern is also present at time zero. With the EC fertiliser, a concern is predicted
in all cases. In acid, sandy soils that are poor in clay and organic matter (PNEC 0,06 mg/kg), a
risk is predicted even if the cadmium content in fertilisers is zero’.

(43)

It is clear that these conclusions refer to the specific situation of the Swedish soil as well as the
climatic conditions prevailing in Sweden.

(44)

In conclusion, the risk assessment carried out by Sweden shows that if fertilisers with a higher
cadmium content than currently permitted would be allowed, this would lead to:

— a substantial increase in the cadmium concentrations of soils, which in turn would lead to toxic
effects on soil organisms. Unacceptable concentrations could also appear in watercourses in
agricultural regions,

— a substantial

increase in the dietary intake of cadmium. The safety margin between current
exposure and the World Health Organisation Provisional Tolerable Weekly Intake level
is
extremely small. For some high-risk groups, such as women with low body iron stores, there are
no safety margins at all. A high dietary intake of cadmium could therefore lead to a larger
number of people becoming subject to reduced kidney function and increased osteoporosis.

2.1.5. Evaluation of the position of Sweden

(45)

The risk assessment submitted by the Swedish authorities has been carried out according to the
procedures and the methodology established at Community level, which are considered to ensure a
high degree of reliability of the information obtained.

(21) PNEC: predicted no effect concentration.
(22) These ratios are PEC/PNEC where PEC is the predicted environmental concentration.
(23) A PEC/PNEC ratio greater than 1 indicates that there will be adverse effects.

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(46)

The Commission already examined the information contained in this risk assessment in the context
of the preparatory work of the proposal for a new Regulation relating to fertilisers (24). At that time,
the Commission considered that the information available provided sufficient indication of a risk for
the environment and human health arising from the application to the Swedish soil of cadmium-
containing fertilisers. The Commission therefore proposed in Article 33 of its proposal an extension
of the derogation already granted to Austria, Finland and Sweden in the Accession Treaty. As the
proposed Regulation could not be adopted in time, Sweden has applied for an individual Decision
under Article 95(6).

(47) After having re-examined the scientific evidence in the light of the Swedish request, the Commission
considers that the Swedish authorities have shown that cadmium-containing fertilisers pose environ-
mental and human health risks, and that the national provisions notified by the Swedish authorities
aiming to limit to the minimum the exposure of the Swedish environment to cadmium-containing
fertilisers are justified.

2.2. ABSENCE OF ARBITRARY DISCRIMINATION

(48) Article 95(6) obliges the Commission to verify that the envisaged measures are not a means of
arbitrary discrimination. According to the ruling of the Court of Justice, the absence of discrim-
ination means that national restrictions on trade cannot be used in such a way as to create
discrimination in respect of goods originating in other Member States.

(49)

The envisaged national provisions are general and apply to national and imported phosphorous-
based EC-designated fertilisers alike. As a result, there is no evidence that they can be used as a
means of arbitrary discrimination between economic operators in the Community.

2.3. ABSENCE OF A DISGUISED RESTRICTION ON TRADE

(50) More restrictive national measures governing the composition of EC-designated fertilisers that
derogate from the provisions of a Community Directive normally constitute a barrier to trade.
Products that can be legally placed on the market in the rest of the Community cannot be placed on
the market in the Member State concerned. The concept enshrined in paragraph 6 of Article 95 is
intended to prevent the national provisions based on the criteria set out in paragraphs 4 and 5 being
applied for inappropriate reasons, and in reality constituting economic measures to be introduced to
impede the import of products from other Member States in order to indirectly protect national
production.

(51) As already established, there is concern with regard to the protection of the environment and human
health due to the application on soil of cadmium-containing fertilisers. Therefore, the protection of
the environment and human health appears to be the goal of maintaining the national provisions
and not the creation of disguised barriers to trade.

2.4. ABSENCE OF OBSTACLES TO THE FUNCTIONING OF THE INTERNAL MARKET

(52)

This condition cannot be interpreted in such a way that it prohibits the approval of any national
measure likely to affect the establishment of the Internal Market. In fact, any national measure
derogating from a harmonisation measure aiming at the establishment and operation of the Internal
Market, constitutes in substance a measure that is likely to affect the Internal Market. Consequently,
to preserve the useful character of the procedure for derogation provided for by Article 95 of the EC
Treaty, the Commission considers that, in the context of Article 95(6), the concept of obstacle to the
functioning of the Internal Market has to be understood as a disproportionate effect in relation to the
pursued objective.

(24) Commission proposal for a European Parliament and Council Regulation relating to fertilisers – COM(2001) 508

final of 14.9.2001.

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(53)

In view of the risks for both the environment and human health resulting from the application of
cadmium-containing fertilisers to the Swedish soil and taking into account that:

— as indicated above, the Act of Accession and Directive 98/97/EC allowed Sweden to continue to
apply its national provisions concerning the cadmium content in fertilisers awaiting the comple-
tion of the review of Directive 76/116/EEC as regards the issue of the cadmium content in
fertilisers, and

— the opinion of the SCTEE was not available in time to be considered for this Decision in order to
provide a sufficient scientific basis for the Commission to propose an approximation of
Community limit values for the cadmium content in fertilisers, or to determine whether there
would be a less restrictive measure,

the Commission considers that, at this stage of the review, there is no evidence indicating that the
national provisions do constitute a disproportionate obstacle to the functioning of the internal
market in relation to the pursued objectives.

2.5. LIMITATION IN TIME

(54)

(55)

(56)

(57)

Sweden asked the Commission to take a decision under Article 95(6) of the Treaty before 31
December 2001. Should the Commission approve the request for a derogation, Sweden asked that
the Decision shall take effect from 1 January 2002.

It should first be noted that given the procedural framework established in Article 95 of the Treaty
and in particular the six-month deadline for a Decision to be adopted, it is incumbent on Member
States to submit a notification to the Commission in time so that the Commission is able to adopt a
decision on the notification before the relevant Community harmonisation measure becomes
enforceable (25).

It should be recalled that the principle of legal certainty, which is a general principle of Community
law, excludes, for the most part, retroactive application of Community legislation, except where the
objective to be achieved requires it and then only on condition that the legitimate expectations of the
parties concerned are respected (26).

In the light of the foregoing, the Commission does not consider that in the present case the
conditions exist for giving a retroactive effect to the Decision approving the national provisions. In
fact, although there is a need to protect human health and the environment from the risks posed by
cadmium in fertilisers, to render the more stringent national measures applicable retroactively would,
in effect, be tantamount to undermining the legitimate expectations of those economic operators
who acted in the belief that the rules in force after 31 December 2001 were the more liberal ones
deriving from Directive 76/116/EEC.

(58)

The period for which the derogation is granted should allow sufficient time for the Commission to
propose and for the Council and the European Parliament to adopt a Legislation concerning
cadmium in fertilisers at Community level. It is estimated that such a Legislation could enter into
force in 2005. The derogation of Sweden should therefore expire on 31 December 2005.

IV. CONCLUSION

(59)

In the light of the foregoing, it can be concluded that the request by Sweden for maintaining national
provisions that are more restrictive than the provisions of Directive 76/116/EEC with regard to the
cadmium content of fertilisers, as submitted on 7 December 2001,

is admissible.

(25) In this connection, it is pointed out that the European Court of Justice, in paragraph 35 of its judgement of 1 June
1999 delivered in case C-319/97, states that ‘it is incumbent on Member States under Article 10 EC (ex Article 5) to
notify as soon as possible the provisions of national law which are incompatible with a harmonisation measure and
which they intend to maintain in force’.

(26) European Court of Justice's judgement of 25 January 1979 delivered in case C-98/78 Racke [1979] ECR 69, para-
graph 20. See also the judgements delivered in the following cases: C-110/97 the Netherlands v Council, [2001] ECR
000, paragraph 151; C-99/78 Decker [1979] ECR 101, paragraph 8; C-258/80 Rummy v Commission [1982] ECR
487, paragraph 11; and C-337/88 SAFA [1990] ECR I-1, paragraph 13.

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Moreover, the Commission finds that the national provisions:
— meet needs on grounds of the protection of human health and the environment;
— are proportionate to the objectives pursued;
— do not constitute a means of arbitrary discrimination and
— do not constitute a disguised restriction on trade between Member States.

The Commission therefore considers that they can be approved,

HAS ADOPTED THIS DECISION:

Article 1

In derogation from Directive 76/116/EEC, the Swedish provisions which prohibit the placing on the
Swedish market of fertilisers containing in excess of 100 grams of cadmium per tonne of phosphorous are
approved.

The derogation shall apply until 31 December 2005.

This Decision is addressed to the Kingdom of Sweden.

Article 2

Done at Brussels, 24 May 2002.

For the Commission

Erkki LIIKANEN

Member of the Commission