Environmental Protection and the Application of Competition Law in Waste Management Issues.


José Rivas
Partner, Abogado
Hammond Suddards Edge, Brussels


Article 6 of the EC Treaty requires that environmental considerations must be integrated into all other areas of Community policy. This commitment was inserted in the EC Treaty by the Treaty of Amsterdam in 1997 and is indicative of the Community's increasing activity in the area of environmental protection. In contrast, the Treaty's commitment to "a system ensuring that competition in the internal market is not distorted " has been one of the cornerstones of the Community and one of the most discussed and analysed areas of European Commission policy from the very beginning of the common market. While one can argue whether or not the Commission is always willing to feel encumbered by the imperative of Article 6, there is no doubt that environmental concerns play a growing role in the Commission's considerations particularly as it is being increasingly called upon to adjudicate on commercial practices relating to environmental protection especially in the area of packaging waste disposal.

This paper will discuss the relevance of the following three areas of competition policy as they have been applied in relation to issues of environmental concern:

  • Agreements between undertakings
  • The abuse of a dominant position
  • The State aid rules

I will conclude with some brief comments on the question of the granting of special or exclusive rights to undertakings.


Agreement Between Undertakings

Article 81(1) EC prohibits collusive agreements, understandings or practices between undertakings, which have as their object or effect the prevention, restriction or distortion of competition . The absolutism of the Article 81(1) prohibition is moderated by the possibility of exemption contained in Article 81(3). Under Article 81(3) such agreements, understandings, or practices which contribute to the improvement of the production or distribution of goods or to the promotion of technical or economic progress, while allowing consumers a fair share of the resulting benefit may be exempted from the Article 81(1) prohibition provided that they are no more restrictive of competition than is necessary to achieve the goals envisaged nor such as to afford the undertakings involved the possibility of eliminating competition in respect of a substantial part of the market for the product in question.

The power to grant exemptions under Article 81(3) is the exclusive competence of the European Commission. It grants such exemptions by two means:

  • Individual exemptions where the Commission produces a decision that a particular agreement notified to it by the parties involved has satisfied the requirements of Article 81(3); or
  • A block exemption under which categories of agreements are exempted from the Article 81(3) prohibition.

The Commission's guidelines on horizontal co-operation agreements.

In order to help undertakings and their legal advisers and in order to give an insight into its policy in applying Article 81 to horizontal agreements, the Commission has published guidelines. Section 7 of these guidelines addresses the area of so-called "Environmental Agreements". By this the Commission means agreements under which the parties undertake to achieve pollution abatement or other environmental objectives, in particular those set out in Article 174 EC. The guidelines specifically mention agreements that set out standards on the environmental performance of products or production processes, as well as agreements between companies at the same level of trade providing for the common attainment of an environmental goal such as the recycling of certain materials, emission reductions or energy-efficiency.

The guidelines acknowledge that agreements that do not impose precise obligations on the parties but which loosely commit them to environmental targets are unlikely to fall under the Article 81(1) prohibition. This also applies to agreements that have only minimal effect on product diversity or purchasing decisions. Furthermore, agreements which give rise to genuine market creation, for instance certain recycling agreements, will not generally be considered to be restrictive of competition provided that, and for as long as, the parties to the agreement would not be capable of pursuing the relevant activities on their own, and provided that other alternatives or competitors do not exist.

Unsurprisingly, the guidelines point out that any environmental agreement between competitors, which is in reality a disguised cartel will always be prohibited. Agreements may be prohibited where they restrict the parties' ability to make decisions regarding the characteristics of their products or the way in which they are produced such as to grant them a way of influencing each other's production and sales. This could apply, for example, in the case of agreements under which parties allocate individual quotas. Agreements whereby parties holding significant market shares appoint an undertaking as an exclusive provider of collection and/or recycling services for their products, may also be considered to be appreciably restrictive of competition provided that actual or potential alternative providers do in fact exist.

In applying the exemption procedure under Article 81(3), the Commission expressly states that it adopts a positive stance on the use of environmental agreements as a policy instrument to achieve the goals enshrined in the Treaty regarding environmental policy. In essence the Commission's analysis is based on the belief that environmental agreements caught by the Article 81(1) prohibition may offer economic benefits both on an individual and collective level that outweigh their negative effects on competition. However, the competitive restrictions must be shown to be indispensable to achieving the environmental goal envisaged as well as being cost-effective.


CECED

An example of a Commission decision granting such an individual exemption is found in CECED . This related to an agreement between manufacturers and importers of washing machines that led to the phasing-out of older models that were less environmentally efficient. In fact the Commission guidelines expressly cite this case as an example of its method of analysis under Article 81(3).

The agreement was caught by Article 81(1) since:

  • It granted the parties control of individual production and imports relating to an appreciable amount of their sales and total output, whilst also reducing third parties' output such as for components and spare parts;
  • Consumer choice was reduced; and
  • Prices would probably rise as a result.

However, exemption was granted under Article 81(3) given that:

  • The newer products were more technically advanced and more environmentally more friendly;
  • The net contribution in terms of environmental improvement outweighed the increased costs;
  • Consumers would recoup the additional costs of the newer machinery as their running costs were lower; and
  • Other alternatives to the agreement were less certain and less cost-effective in delivering the same net benefits.

Eco-Emballages.

In July 2001 the Commission cleared the contracts concluded by the French company Eco- Emballages concerning its system of selective collection and recovery of household waste . This system was intended to meet the obligations imposed on firms by the French Decree 92-377 and by EC Directive 94/62 on packaging and packaging waste. Under the scheme, the producers pay a financial contribution to Eco-Emballages in return for having their legal obligations in the area of the recycling of packaging discharged. Eco-Emballages then redistributes the money to the local authorities that are responsible for the collection of household waste in their local areas. This flow of funds to the authorities is intended to compensate them for the additional cost of having to selectively collect and sort this type of waste. The local authorities then sell the sorted waste to private companies, which recover it.

Eco-Emballages notified the agreements establishing their system in December 1993. In 2000 it was informed by the Commission that certain amendments would need to be made to the various contracts involved. These amendments were made and the Commission issued a negative clearance. The key changes made related to the duration and scope of the agreements as well as to the granting of sub-licences for the use of the 'Green Dot' logo.

Under the amended contracts:

  • Producers may now leave the system after a year and at the end of every subsequent year;
  • Local authorities may immediately terminate their contracts with the Eco-Emballage, while Eco-Emballages must honour their side of the contract for the full term of six years in the absence of any default on the part of the local authorities;
  • Producers may now conclude a contract for all or only some of their packaging and local authorities may conclude an agreement for all or only some of the packaging waste materials they collect;
  • The possibility of using the "Green Dot" logo is offered to all undertakings that legitimately need to use this symbol to carry on business. Adelphe, Eco-Emballage's main competitor, has obtained such a sub-licence to use the Green Dot in its system;
  • Eco-Emballages has furthermore agreed to grant such sub-licences even to undertakings that wish to make individual arrangements for some or all of their packaging while availing of another system either in the rest of France or in other countries.
Duales System Deutschland.

In September 17 2001, three months after the Commission's decision regarding Eco-Emballages, and some six months after finding that the company abused its dominant position (as discussed in the next section), the Commission granted negative clearance to the notified statutes of Duales System Deutschland (DSD) .

DSD is the only undertaking in Germany operating a comprehensive packaging take-back system. The system is intended to meet the requirements of the German packaging ordinance and EC Directive 94/62 on packaging and packaging waste. Under the ordinance every distributor and manufacturer using sales packaging is obliged to take back free of charge used sales packaging from customers at, or in the vicinity of, the point of sale. However undertakings may delegate this responsibility to third parties which will fulfil this responsibility for them (so-called "self-management solutions") or may even be excused from the take back obligation where they participate in a comprehensive system such as that of DSD which guarantees regular collections of used sales packaging from the final consumer. Membership of the DSD scheme is centred on a trade mark agreement between DSD and its customers under which the customers are licensed to display the distinctive Green Dot on their packaging and DSD guarantees the participating company that it will collect, sort and recycle used sales packaging in such a manner as to fulfil the requirements of the packaging ordinance.

DSD does not perform the collection tasks itself but rather contracts this work out to local collecting companies. Once the waste is collected and sorted it is then conveyed directly to a recycling plant either by the collector or is handed over to so-called guarantee companies, which have given DSD an assurance that they will recycle the waste.

The Commission recognised three competition concerns in addressing the DSD agreements:

  • The free marketing of secondary material: Collected and sorted packaging material can be reused as a secondary raw material for various new products. Under DSD's original agreements the collector was not entitled to market the collected material itself. The Commission objected to this restraint on the basis that it threatened to give DSD and its guarantee companies a dominant position on the market for secondary raw material. The collectors are now free to market the collected and sorted waste.
  • ·

  • The duration of service agreements: In the agreements as originally notified to the Commission the service agreements between DSD and its local collectors were concluded for periods of up to 15 years. Given the fact that DSD had only one collector per district and was the only provider of a comprehensive recycling system in the country, contracts of such duration were sufficient to foreclose the market. In response to the Commission's concerns, DSD set a termination date of 31 December 2003 for the agreements which meant that in effect the longest lasting of the agreements would be terminated after 11 years.
  • Access to collection infrastructure: The Commission's investigation concluded that the collection and sorting of household packaging waste is characterised by a number of features which make the duplication of existing collection infrastructure economically unviable. Therefore to ensure the existence of competition in the downstream market for organising the takeback and recovery of used sales packaging, DSD agreed to provide unrestricted access to, and unlimited sharing of, its collection facilities by its competitors.
Abuse of Dominance

Duales System Deutschland.
Article 82 EC prohibits abusive unilateral behaviour by an undertaking holding a dominant market position in a significant part of the Common Market. Its potential application in the field of packaging and waste management is illustrated by the Commission's recent decision in DSD .

In its decision the Commission found DSD to hold a quasi-monopoly, with over 80% of the market. The so-called "self management" solutions, mentioned above, provided no more than competition at the fringes.

The Commission objected to a provision of the agreement between DSD and its customers under which DSD had to pay fees that corresponded to the volume of the packaging sold in Germany bearing the Green Dot rather than the quantity of packaging recycled. Thus the Commission held that the system did not uphold the principle of "no use no fee". The Commission held that an abuse of a dominant position occurred every time an undertaking that :
a) decided to avail of DSD's exemption service in respect of only part of its packaging waste in Germany; or
b) chose not to avail of DSD's service at all in Germany while still participating in recycling systems which used the Green Dot mark in other Member States and wished to use the same Green Dot bottles as it used elsewhere ,
was charged fees by DSD for the total volume of packaging the undertaking released onto the German market.

DSD maintained that such undertakings were under an obligation to pay collection and retrieval fees to it in respect of all packaging used in Germany bearing the Green Dot symbol since it owns the sole rights to the Green Dot logo in that country. Such a scenario, the Commission concluded, led inevitably to a double payment situation where the licencee had to pay both DSD and the company that actually provided the waste management service.

The Commission further concluded that obliging undertakings not to mark packaging that was not to be covered by the DSD system in Germany with the Green Dot was not realistic as this would oblige them to produce at least two different packaging lines, the additional cost of which could well offset the advantage of availing of the services of DSD's competitors.

State Aid - The Example of Ecotaxes

Article 87 EC sets out the principles on the basis of which the compatibility of State aids with the common market is to be judged. Article 87(1) enunciates the general principle that State aids fulfilling certain broadly defined criteria are incompatible with the common market. This general principle is qualified by "ipso jure" exceptions, listed in paragraph (2) and discretionary exceptions listed in paragraph (3).

For the purposes of today's discussion I would like to consider briefly the Community's State aid discipline as applied to the question of derogations from so-called ecotaxes. As in the area of horizontal relationships between undertakings as discussed earlier with regard to the Article 81(1) prohibition, the Commission has issued Guidelines on the grant of State aid for environmental protection.

Guidelines on State aid for environmental protection.

The Commission's first guidelines in this area were adopted in 1994 for a period of five years. However these guidelines were subsequently prolonged for another two years and it was not until 2001 that new guidelines were adopted . They are a useful starting point for anybody wishing to get to grips with Community policy in this area.

Paragraphs 22 to 24 of the guidelines specifically address the question of ecotaxes as applied in the energy sector. The Commission noted the developing trend among Member States of adopting taxes in order to encourage the protection of the environment. The guidelines go on to note that in some cases exemptions from or reductions in taxes are granted to firms in particular categories in order to avoid placing them in a 'difficult competitive position'. The guidelines are clear that such exemptions or reductions are capable of constituting State aid. However the negative effect of such aid may be offset by the benefits accrued. Therefore where such exemptions or reductions are considered necessary to ensure the adoption or continued application of the taxes applicable to products in general, the Commission takes the position that they are acceptable provided that they are subject to certain conditions and last only for a limited period of time. Under the guidelines this period may last for up to 10 years although the Member State in question is free to re-notify its arrangements to the Commission after the expiry of that period.

Paragraphs 47 to 53 of the Guidelines go on to consider the rules applicable to operating aid granted in the form of reductions in or exemptions from environmental taxes. Operating aid is aid that is not justified under any of the Commission's guidelines or regulations and is purely intended to reduce a firm's current expenses. The Commission's guidelines consider two scenarios:

Scenario 1: A Tax Imposed as a Result of a State Measure.

If the tax levied is purely an autonomous measure taken by a Member State then the Commission accepts that firms affected may have difficulty adapting rapidly to the tax burden. In such circumstances there may be justification for a temporary reduction or exemption enabling certain firms to adapt to the change and in such cases the exemption will be compatible with the common market. From the Guidelines the key consideration would seem to be whether, in the absence of the possibility of a reduction or an exemption for the particularly sensitive industries, the entire scheme would be feasible.

Scenario 2: A Tax Imposed as a Result of Community Harmonisation.

In the case of a tax resulting from a Community measure two further scenarios are envisaged:

1. A Member State applies tax to certain products at a rate higher than the minimum rate laid down in the Community directive and grants an exemption to certain firms which, as a result pay tax at a rate which is lower, but still at least equal to the minimum tax set by the directive. The Commission sees such variations are justified to enable firms to adapt to the higher taxation;

2. A Member State applies tax to certain products at the minimum rate laid down in the directive and grants an exemption to certain firms, which are therefore subject to the tax at a rate lower than the minimum. If such an exemption is not authorised by the directive in question, it will constitute aid incompatible with the common market. If it is allowed for under the directive then it will be compatible with Treaty rules in so far as it is necessary and not disproportionate in light of the community objectives pursued.

The German Situation.

For an example of the approach taken by the Commission in applying these principles, we might consider the situation of ecotax derogations notified to the Commission by the authorities in Germany. In 1999 the German government notified to the Commission its ecotax laws, which provided for reduced tax rates for the producing industry, the agriculture and forestry sector and for rail transport services . Thus while all companies had to pay a higher rate than before, companies in these sectors paid less than that applied to companies in general. While the Commission acknowledged that such a benefit favouring certain industries or sectors may have to be considered to be State aid, it decided not to raise any objection to the German scheme since it was in line with the 1994 guidelines which recognised that such State aid could be approved in cases where the application of the general rate would affect the competitive position of certain undertakings. Germany agreed to renotify the scheme after three years.

Since then the German authorities have progressively raised the levels of these ecotaxes while maintaining derogations for energy intensive industries. In February of this year the Commission gave its decision on Germany's renotified arrangements . While the Commission's decision to approve the latest German programme covers a number of reductions relating to various taxes, a number are worth emphasising in particular as they exemplify the Commission' s approach under the Guidelines on State aid for environmental protection:

· An 80% reduction to be applied for ten years to the increase in the mineral oil tax for heating purposes for the production sector, including companies active in sectors covered under the ECSC Treaty, agriculture, forestry and fishery. This measure has been held to be compatible since the rate of tax levied is still higher than the minimum as set out in the Council Directive 92/81/EEC of 19 October 1992 on the harmonisation of the structures of excise duties;

· A favourable tax treatment of Combined Heat and Power (CHP) installations as regards their input fuel requirements of oil and gas was held to fulfil the requirements of the guidelines insofar as the measure constituted State aid. Paragraph 31and 66 of the guidelines combine to approve of both operating and investment aid for CHP as long as it can be shown that:
The conversion efficiency (the ratio between the quantity of primary energy used and the amount of secondary energy produced) is particularly high;
The measures will lead to a reduction in the overall amount of energy produced; or
The production process will be less damaging to the environment.

The Grant of Special or Exclusive Rights.

As a final point I would just like to note that the Community competition rules do not prevent a Member State from granting (a) selected undertaking(s) special or exclusive rights, even if such a grant amounts to the award of a monopoly position to a particular undertaking. One could feasibly imagine a scenario in which a Member State might choose to grant such a right in the case of a nationwide recycling system.
Under Article 86 (1) EC, Member States are obliged not to enact nor maintain in force any measure contrary to the Treaty rules, including those relating to competition, in relation to public undertakings or undertakings to which the Member State has granted special or exclusive rights. However, Article 86(2) states that undertakings entrusted with the operation of services of a general economic interest or undertakings having the character of a revenue-producing monopoly shall only be subject to the rules of the Treaty, including those relating to competition in so far as the application of such rules do not obstruct the performance of the particular tasks applied to them.
In principle the mere grant of an exclusive right is not incompatible with the EC Treaty and only the abuse is subject to Article 82. However the Court of Justice has found that the grant of such rights may infringe the Community rules if:
· It results in discrimination against imports or the cross border provision of services ;
· The undertaking enjoying these rights is manifestly incapable of satisfying market demand ; or
· The grant of exclusive rights to an undertaking induces that undertaking to breach Article 82 EC . An example of one such situation arose where one operator in the market for dock-work services in the Port of Genoa was given the exclusive right to supply its competitors with temporary labour . The Court of Justice judged the undertaking to be thus placed in a situation wherby the mere exercise of its monopoly would lead to an abuse of its position given that it would certainly retain the best staff for itself.

Conclusions.

It is likely that the coming years will see the European Commission increasingly called upon to apply environmental thinking in formulating competition policy. The plethora of initiatives witnessed in fields such as waste recycling, whether initiated as a result of national or European legislation, have seen the emergence of new operations, which while environmentally beneficial, may not sit easily in the existing competition framework. Formulating effective competition models, which can serve the twin imperatives, set forth in the Treaty of free competition and environmental protection is in its early days. However it looks likely to be an engaging topic of analysis and debate for years to come.



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