3. The European Commission’s Infringement Mechanism

The European Commission is the guardian of its Treaties. As such, it has a responsibility to ensure proper implementation and enforcement of EU law, i.e. the acquis communautaire. The Commission identifies possible infringements of EU law on the basis of its own investigations or following complaints from citizens, businesses or other stakeholders. It may refer to any measure (law, regulation or administrative action) or the absence of a measure or practice by a country of the European Union that is against Union law. The European Commission can only take up the complaint if it is about a breach of Union law by authorities in an EU country (not by a private individual or body).

A complaint must be submitted via the standard complaint form 42 . The complaint may be submitted in any official EU language and should include the following details:

  • description of how national authorities have infringed Union law, and which is the Union law infringed;
  • details of any steps already taken to obtain redress.

Complaints to the European Commission go through the following process 43 :

  • The European Commission will confirm that it has received your complaint within 15 working days.
  • Within the following 12 months, the European Commission will assess your complaint and aim to decide whether to initiate a formal infringement procedure against the country in question.
  • If the issue raised is particularly complicated, or if the European Commission needs to ask for more information or details, it may take longer than 12 months to reach a decision.
  • If the European Commission decides that the complaint is well-founded and initiates a formal infringement procedure against the country in question, it will inform the complainant about case progresses.
  • Should the Commission contact the authorities of the country against which the complaint is made, it will not disclose the identity of the complainant unless permission is given.
  • At any time, the complainant may give the European Commission additional material about the complaint or ask to meet representatives of the European Commission.

A formal infringement procedure follows a number of steps, each ending with a formal decision 44 :

  • The Commission sends a letter of formal notice requesting further information to the country concerned. The latter must send a detailed reply within a specified period, usually two months.
  • If the Commission concludes that the country is failing to fulfil its obligations under EU law, it may send a reasoned opinion: a formal request to comply with EU law. It explains why the Commission considers that the country is breaching EU law and requests, that the country informs the Commission of the measures taken within a specified period, usually two months.
  • If the country still does not comply, the Commission may decide to refer the matter to the Court of Justice. Most cases are settled before being referred to the Court.
  • If the Court finds that a country has breached EU law, the national authorities must take action to comply with the Court’s judgment.
  • If, despite the Court’s judgment, the country still does not rectify the situation, the Commission may refer the country back to the Court.
  • When referring an EU country to the Court for the second time, the Commission proposes that the Court imposes financial penalties, which can be either a lump sum and/or a daily payment.

CASE LAW EXAMPLE

Case C-441/17 European Commission v Republic of Poland 45

The following Case law example presents a ruling of the Court of Justice indicating that the Republic of Poland did not comply with the Habitats Directive when it started the logging of trees in a Natura 2000 site.

In July 2017 the European Commission referred Poland to the Court of Justice and requested interim measures to stop increased logging operations in the Białowieża Forest – one of Europe’s last remaining primeval forest, which is a protected Natura 2000 site. The removal of century old trees posed a major threat to the integrity of this Natura 2000 site. The site protects species and habitats that are dependent on old-growth forests, including the availability of dead wood. For some of these species, the Białowieża Forest is the most important or the last remaining site in Poland.

As logging operations have started on a significant scale, the Commission also requested the Court for interim measures compelling Poland to suspend the works immediately. According to EU law, the Court of Justice can prescribe interim measures to require a Member State to hold back from activities causing serious and irreparable damage before a judgement is given.

In the case C-441/17 European Commission v Republic of Poland the Court of Justice, first issued the emergency ban on logging in Bialowieza Forest, saying it will impose fines of at least €100,000 a day if Poland’s Environment Minister keeps ignoring the Court’s decisions, and later ruled that the Republic of Poland has failed to fulfil its obligations under the Habitats and Birds Directives.

footnote 67

Convention on the Conservation of European Wildlife and Natural Habitats,
https://www.coe.int/en/web/conventions/full-list/-/conventions/treaty/104

footnote 64

Guidance on the Application of the Environmental Impact Assessment Procedure for Large-scale Transboundary Projects: http://ec.europa.eu/environment/eia/pdf/Transboundry%20EIA%20Guide.pdf

footnote 63

Guidance on Public Participation in Environmental Impact Assessment in a Transboundary Context: https://www.unece.org/fileadmin/DAM/env/documents/2006/eia/ece.mp.eia.7.pdf

footnote 62

Guidance on the Application of the Environmental Impact Assessment Procedure for Large-scale Transboundary Projects: http://ec.europa.eu/environment/eia/pdf/Transboundry%20EIA%20Guide.pdf

footnote 54

United Nations Economic Commission for Europe, The Aarhus Convention: An implementation guide, 2014

footnote 50

Directive 2001/42/EC of the European Parliament and of the Council of 27 June 2001 on the assessment of the effects of certain plans and programmes on the environment (transposition by 1 January 2018 and implementation by 31 March 2018)

footnote 49

Directive 2004/35/EC of the European Parliament and of the Council of 21 April 2004 on environmental liability with regard to the prevention and remedying of environmental damage, as amended by Directive 2006/21/EC, Directive 2009/31/EC and Directive 2013/30/EU (implementation by 1 January 2021)

footnote 48

Directive 79/409/EEC of the Council of 2 April 1979 on the conservation of wild birds (implementation on the entry into force of the Treaty i.e. 1 July 2006)

footnote 47

Council Directive 85/337/EEC of 27 June 1985 on the assessment of the effects of certain public and private projects on the environment, as amended by Council Directives 97/11/EC of 3 March 1997 (implementation on the entry into force of the Treaty i.e. 1 July 2006), Directive 2011/92/EU of the European Parliament and of the Council of 13 December 2011 on the assessment of the effects of certain public and private projects on the environment (implementation by 14 October 2016) and Directive 2014/52/EU (implementation by 1 January 2019)

footnote 40

The habitats and species concerned are defined by reference to species and types of natural habitats identified in the relevant parts of the Birds Directive and the Habitats Directive. The scope of the ELD is not restricted to the Natura 2000 network. The species mentioned in ELD which occur outside the SACs and SPAs and even migratory species are also included

footnote 39

The significance of any damage that has adverse effects on reaching or maintaining the favourable conservation status of habitats or species has to be assessed by reference to the conservation status at the time of the damage, the services provided by the amenities they produce and their capacity for natural regeneration. Significant adverse changes to the baseline condition should be determined by means of measurable data such as:

  • the number of individuals, their density or the area covered;
  • the role of the particular individuals or of the damaged area in relation to the species or to the habitat conservation, the rarity of the species or habitat (assessed at local, regional and higher level including at Community level);
  • the species’ capacity for propagation (according to the dynamics specific to that species or to that population), its viability or the habitat’s capacity for natural regeneration (according to the dynamics specific to its characteristic species or to their populations);
  • the species’ or habitat’s capacity, after damage has occurred, to recover within a short time, without any intervention other than increased protection measures, to a condition which leads, solely by virtue of the dynamics of the species or habitat, to a condition deemed equivalent or superior to the baseline condition.

Damage with a proven effect on human health must be classified as significant damage. The following does not have to be classified as significant damage:

  • negative variations that are smaller than natural fluctuations regarded as normal for the species or habitat in question;
  • negative variations due to natural causes or resulting from intervention relating to the normal management of sites, as defined in habitat records or target documents or as carried on previously by owners or operators;
  • damage to species or habitats for which it is established that they will recover, within a short time and without intervention, either to the baseline condition or to a condition which leads, solely by virtue of the dynamics of the species or habitat, to a condition deemed equivalent or superior to the baseline condition.

footnote 38

Damage took place not earlier than 30 April 2007 or the activity causing the damage was finished not earlier than 30 April 2007, or less than 30 years have passed since the emission, event or incident, resulting in the damage, occurred

footnote 32

See C-664/15, Protect, paragraph 81

footnote 31

See C-664/15, Protect, paragraph 102

footnote 30

CIS Guidance no 36 Exemptions to the Environmental Objectives according to Article 4(7):
https://circabc.europa.eu/sd/a/e0352ec3-9f3b-4d91-bdbb-939185be3e89/CIS_Guidance_Article_4_7_FINAL.PDF

footnote 28

See C-461/13, Bund für Umwelt und Naturschutz Deutschland e.V. v Bundesrepublik Deutschland

footnote 27

This includes new modifications to the physical characteristics of a surface water body, alterations to the level of groundwater, and new sustainable human development activities

footnote 24

See C-127/02, Waddenzee, paragraphs 66 – 70. In case C-243/15, the Court of Justice also confirmed that decisions adopted by the competent national authorities within the framework of Article 6(3) of Directive 92/43 (whether they concern a request to participate in the authorisation procedure, the assessment of the need for an environmental assessment of the implications of a plan or project for a protected site, or the appropriateness of the conclusions drawn from such an assessment as regards the risks of that plan or project for the integrity of the site, and whether they are autonomous or integrated in a decision-granting authorisation) are decisions, which fall within the scope of Article 9(2) of the Aarhus Convention

footnote 23

Guidance on the requirements for hydropower in relation to Natura 2000, p. 70: http://ec.europa.eu/environment/nature/natura2000/management/docs/Hydro%20final%20May%202018.final.pdf

footnote 22

Guidance on the requirements for hydropower in relation to Natura 2000: http://ec.europa.eu/environment/nature/natura2000/management/docs/Hydro%20final%20May%202018.final.pdf

footnote 21

See C-127/02, Waddenzee, paragraphs 66 – 70. In case C-243/15, the Court of Justice also confirmed that decisions adopted by the competent national authorities within the framework of Article 6(3) of Directive 92/43 (whether they concern a request to participate in the authorisation procedure, the assessment of the need for an environmental assessment of the implications of a plan or project for a protected site, or the appropriateness of the conclusions drawn from such an assessment as regards the risks of that plan or project for the integrity of the site, and whether they are autonomous or integrated in a decision-granting authorisation) are decisions, which fall within the scope of Article 9(2) of the Aarhus Convention

footnote 20

See, C-243/15, Lesoochranárske zoskupenie VLK v Obvodný úrad Trenčín (Slovak Bears II), para 46-49

footnote 18

See Commission Notice on Access to Justice in Environmental Matters, https://ec.europa.eu/environment/aarhus/pdf/notice_accesstojustice.pdf

footnote 17

See C-474/10 – Seaport (NI) and others, paragraphs 45 and 50

footnote 16

See C-295/10, Valčiukienė and Others, paragraphs 44-47 and 53

footnote 13

Environmental Impact Assessment of Projects Guidance on the preparation of the Environmental Impact Assessment Report: http://ec.europa.eu/environment/eia/pdf/EIA_guidance_EIA_report_final.pdf

footnote 12

See C-75/08, Mellor, paragraph 64

footnote 10

See C-66/06, Commission v Ireland, paragraph 64

footnote 11

See C-87/02, Commission v Italy, paragraph 49

footnote 09

See for example C-66/06, Commission v Ireland; C-255/08, Commission v Netherlands; C-435/09, Commission v Belgium

footnote 02

The EU’s ‘acquis’ is the body of common rights and obligations that are binding for all EU Member States. It constantly evolves and comprises: the content, principles and political objectives of the Treaties; legislation adopted in application of the treaties and the case law of the Court of Justice of the EU; declarations and resolutions adopted by the EU; measures relating to the common foreign and security policy; measures relating to justice and home affairs; international agreements concluded by the EU, as well as those concluded by EU countries between themselves in fields relevant to the EU’s activities.
(https://eur-lex.europa.eu/summary/glossary/acquis.html)

footnote 01

The rule of law is one of the EU’s fundamental values. It is the idea that both the EU itself and all EU countries are governed by a body of law (legal codes and processes) adopted by established procedures, rather than discretionary or case-by-case decisions.
(https://eur-lex.europa.eu/summary/glossary/rule_of_law.html)