COMMON POSITION (EC) No 49/98 adopted by the Council on 4 June 1998 with a view to adopting Council Directive 98/ /EC, of ... on the landfill of waste
30. 10. 98 EN Official Journal of the European Communities C 333/15 COMMON POSITION (EC) No 49/98 adopted by the Council on 4 June 1998 with a view to adopting Council Directive 98/ /EC, of. on the landfill of waste (98/C 333/02) THE COUNCIL OF THE EUROPEAN UNION, Having regard to the Treaty establishing the European Community, and in particular Article 130s(1) thereof, Having regard to the proposal from the Commission (1), Having regard to the opinion of the Economic and Social Committee (2), Acting in accordance with the procedure laid down in Article 189c of the Treaty (3), (1) Whereas the Council resolution of 7 May 1990 (4) on waste policy welcomes and supports the Community strategy document and invites the Commission to propose criteria and standards for the disposal of waste by landfill; (2) Whereas the Council resolution of 9 December 1996 on waste policy considers that, in the future, only safe and controlled landfill activities should be carried out throughout the Community; (3) Whereas the prevention, recycling and recovery of waste should be encouraged as should the use of recovered materials and energy so as to safeguard natural resources and obviate wasteful use of land; the (4) Whereas further consideration should be given incineration of municipal to and composting, biomethanisation, and the processing of dredging sludges; issues of non-hazardous waste, (5) Whereas under the polluter pays principle it is necessary, inter alia, to take into account any damage the environment produced by a landfill; to (1) OJ C 156, 24. 5. 1997, p. 10. (2) OJ C 355, 21. 11. 1997, p. 4. (3) Opinion of the European Parliament of 19 February 1998 (OJ C 80, 16. 3. 1998, p. 204), Council Common Position of 4 June 1998 and European Parliament Decision of. (not yet published in the Official Journal). (4) OJ C 122, 18. 5. 1990, p. 2. (6) Whereas, like any other type of waste treatment, landfill should be adequately monitored and managed to prevent or reduce potential adverse effects on the environment and risks to human health; (7) Whereas it to disposal is necessary take appropriate measures to avoid the abandonment, dumping or uncontrolled of waste; whereas, accordingly, it must be possible to monitor landfill sites with respect to the substances contained in the waste deposited there; whereas such substances should, as far as possible, react only in foreseeable ways; (8) Whereas both the quantity and hazardous nature of waste intended for landfill should be reduced where appropriate; whereas the handling of waste should be facilitated and its recovery enhanced; whereas the use of treatment processes should therefore be encouraged to ensure that landfill is compatible with the objectives of this Directive; whereas sorting is included in the definition of treatment; (9) Whereas Member States should be able to apply the principles of proximity and self-sufficiency for the elimination of their waste at Community and national level, in accordance with Council Directive 75/442/EEC of 15 July 1975 on waste (5); whereas the objectives of this Directive must be pursued and clarified through the establishment of an adequate, integrated network of disposal plants based on a high level of environmental protection; (10) Whereas disparities between technical standards for the disposal of waste by landfill and the lower costs associated with it might give rise to increased disposal of waste in facilities with low standards of environmental protection and thus create a potentially serious threat to the environment, owing to transport of waste over unnecessarily long distances as well as to inappropriate disposal practices; (11) Whereas it is therefore necessary to lay down technical standards for the landfill of waste at Community level in order to protect, preserve and improve the quality of the environment in the Community; (5) OJ L 194, 25. 7. 1975, p. 39. Directive as last amended by Commission Decision 96/350/EC (OJ L 135, 6. 6. 1996, p. 32). C 333/16 EN Official Journal of the European Communities 30. 10. 98 (12) Whereas it is necessary to indicate clearly the requirements with which landfill sites must comply as regards location, conditioning, management, control, closure and preventive and protective measures to be taken against any threat to the environment in the short as well as in the long-term perspective, and more especially against the pollution of groundwater by leachate infiltration into the soil; (13) Whereas in view of the foregoing it is necessary to define clearly the classes of landfill to be considered and the types of waste to be accepted in the various classes of landfill; (14) Whereas sites for temporary storage of waste should comply with the relevant requirements of Directive 75/442/EEC; (15) Whereas the recovery, in accordance with Directive inert or non-hazardous waste 75/442/EEC, of which in redevelopment/restoration and filling-in work, or for construction purposes may not constitute a landfilling activity; their use suitable, through is (16) Whereas measures should be taken to reduce the production of methane gas from landfills, inter alia, in order to reduce global warming, through the reduction of the landfill of biodegradable waste and the requirements to introduce landfill gas control; (17) Whereas the measures taken to reduce the landfill of biodegradable waste should also aim at encouraging of biodegradable waste, sorting in general, recovery and recycling; collection separate the (18) Whereas, because of the particular features of the landfill method of waste disposal, it is necessary to introduce a specific permit procedure for all classes of landfill in accordance with the general licensing requirements already in Directive 75/442/EEC and the general requirements of Directive 96/61/EC concerning integrated pollution prevention and control (1); whereas the landfill site’s compliance with such a permit must be verified in the course of an inspection by the competent authority before the start of disposal operations; set down (19) Whereas, in each case, checks should be made to establish whether the waste may be placed in the landfill for which it is intended, in particular as regards hazardous waste; (1) OJ L 257, 10. 10. 1996, p. 26. (20) Whereas, in order to prevent threats to the environment, it is necessary to introduce a uniform waste acceptance procedure on the basis of a classification procedure for waste acceptable in the different categories of in particular standardised limit values; whereas to that end a consistent and standardised system of waste characterisation, sampling and analysis must be established in time to facilitate implementation of this Directive; whereas the acceptance criteria must be particularly specific with regard to inert waste; including landfill, (21) Whereas, pending the establishment of such methods of analysis or of the limit values necessary for characterisation, Member States may for the purposes of this Directive maintain or draw up national lists of waste which is acceptable or unacceptable landfill, or define criteria, including limit values, similar to those laid down in this Directive acceptance procedure; the uniform for for (22) Whereas for certain hazardous waste to be accepted in landfills for non-hazardous waste acceptance criteria should be developed by the technical committee; (23) Whereas it is necessary to establish common monitoring procedures during the operation and aftercare phases of a landfill in order to identify any possible adverse environmental effects of the landfill and the appropriate corrective measures; take (24) Whereas it is necessary to define when and how a landfill should be closed and the obligations and responsibility of the operator on the site during the aftercare period; (25) Whereas landfill sites that have been closed prior to the date of transposition of this Directive should not be subject its provisions on closure procedure; to (26) Whereas the future conditions of operation of existing landfills should be regulated in order to take the necessary measures, within a specified period of time, for their adaptation to this Directive on the basis of a site-conditioning plan; (27) Whereas for operators of existing landfills having, in rules compliance with binding national equivalent to those of Article 14 of this Directive, already submitted the documentation referred to in Article 14(a) of this Directive prior to its entry into force and for which the competent authority authorised the continuation of their operation, 30. 10. 98 EN Official Journal of the European Communities C 333/17 there is no need to resubmit this documentation nor for the competent authority to deliver a new authorisation; HAS ADOPTED THIS DIRECTIVE: (28) Whereas the operator should make adequate provision by way of a financial security or any other equivalent to ensure that all the obligations flowing from the permit are fulfilled, including the closure procedure and to those relating aftercare of the site; (29) Whereas measures should be taken to ensure that the price charged for waste disposal in a landfill covers all the costs involved in the setting up and operation of the facility, including as far as possible the financial security or its equivalent which the site operator must provide, and the estimated cost of closing the site including the necessary aftercare; (30) Whereas, when a competent authority considers that a landfill is unlikely to cause a hazard to the environment for longer than a certain period, the estimated costs to be included in the price to be charged by an operator may be limited to that period; (31) Whereas it is necessary to ensure the proper application of the provisions implementing this Directive throughout the Community, and to ensure that the training and knowledge acquired by landfill operators and staff afford the necessary skills; them (32) Whereas the Commission must establish a standard procedure for the acceptance of waste and set up a standard classification of waste acceptable in a landfill committee procedure laid down in Article 18 of Directive 75/442/EEC; in accordance with the (33) Whereas adaptation of the Annexes this Directive to scientific and technical progress and the standardisation of the monitoring, sampling and analysis methods must be adopted under the same committee procedure; to (34) Whereas the Member States must send regular reports to the Commission on the implementation of this Directive paying particular attention to the national strategies to be set up pursuant to Article 5; whereas on the basis of these reports the Commission the European report Parliament and the Council, shall to Article 1 Overall objective 1. With a view to meeting the requirements of Directive 75/442/EEC, and in particular Articles 3 and 4 thereof, the aim of this Directive is, by way of stringent operational and technical requirements on the waste and landfills, to provide for measures, procedures and guidance to prevent or reduce as far as possible negative effects on the environment, in particular the pollution of surface water, groundwater, soil and air, and on the global environment, including the greenhouse effect, as well as any resulting risk to human health, from landfilling of waste, during the whole life cycle of the landfill. In respect of the technical characteristics of landfills, 2. this Directive contains, for those landfills to which Directive 96/61/EC is applicable, the relevant technical requirements in order to elaborate in concrete terms the general requirements of that Directive. The relevant requirements of Directive 96/61/EC shall be deemed to be fulfilled if the requirements of this Directive are complied with. Article 2 Definitions For the purposes of this Directive: (a) ‘waste’ means any substance or object which is covered by Directive 75/442/EEC; (b) (c) ‘municipal waste’ means waste from households, as well as other waste which, because of its nature or composition, is similar to waste from households; ‘hazardous waste’ means any waste which is covered by Article 1(4) of Council Directive 91/689/EEC of 12 December 1991 on hazardous waste (1); (d) ‘non-hazardous waste’ means waste which is not covered by paragraph (c); (e) ‘inert waste’ means waste that does not undergo any significant biological transformations. Inert waste will not dissolve, burn react, or otherwise physically or chemically physical, chemical or (1) OJ L 377, 31. 12. 1991, p. 20. Directive as last amended by Directive 94/31/EC (OJ L 168, 2. 7. 1994, p. 28). C 333/18 EN Official Journal of the European Communities 30. 10. 98 biodegrade or adversely affect other matter with which it comes into contact in a way likely to give rise to environmental pollution or harm human health. The total leachability and pollutant content of the waste and the ecotoxicity of the leachate must be insignificant, and in particular not endanger the quality of surface water and/or groundwater; (f) ‘underground storage’ means a permanent waste storage facility in a deep geological cavity such as a salt or potassium mine; (g) ‘landfill’ means a waste disposal site for the deposit of the waste onto or into land (i. e. underground), including: — internal waste disposal sites (i. e. landfill where a producer of waste is carrying out its own waste disposal at the place of production), and — a permanent site (i. e. more than one year) which is used for temporary storage of waste, but excluding: — facilities where waste is unloaded in order to permit its preparation for further transport for recovery, treatment or disposal elsewhere, and — storage of waste prior to recovery or treatment for a period less than three years as a general rule, or — storage of waste prior to disposal for a period less than one year; (h) ‘treatment’ means the physical, thermal, chemical or biological processes, including sorting, that change the characteristics of the waste in order to reduce its volume or hazardous nature, facilitate its handling or enhance recovery; (m) ‘biodegradable waste’ means any waste that is capable of undergoing anaerobic or aerobic decomposition, such as food and garden waste, and paper and paperboard; (n) ‘holder’ means the producer of the waste or the natural or legal person who is in possession of it; (o) ‘applicant’ means any person who applies for a landfill permit under this Directive; (p) ‘competent authority’ means that authority which the Member States designate as responsible for performing the duties arising from this Directive; (q) ‘liquid waste’ means any waste in liquid form including waste waters but excluding sludge; (r) ‘isolated settlement’ means a settlement: — with no more inhabitants per than 500 municipality or settlement and no more than five inhabitants per square kilometre, and — where the distance the nearest urban to agglomeration with at least 250 inhabitants per square kilometre is not less than 50 km, or with difficult access by those nearest agglomerations, due to harsh meteorological conditions during a significant part of the year. road to Article 3 Scope 1. Member States shall apply this Directive to any landfill as defined in Article 2(g). existing Community 2. Without legislation, the following shall be excluded from the scope of this Directive: prejudice to (i) ‘leachate’ means any liquid percolating through the deposited waste and emitted from or contained within a landfill; — the spreading of sludges, including sewage sludges, and sludges resulting from dredging operations, and similar matter on the soil for the purposes of fertilisation or improvement, (j) ‘landfill gas’ means the gases generated from the landfilled waste; (k) ‘eluate’ means the solution obtained by a laboratory leaching test; (l) the natural or ‘operator’ means legal person responsible for a landfill in accordance with the internal legislation of the Member State where the landfill is located; this person may change from the preparation to the aftercare phase; — the use of inert waste which in redevelopment/restoration and filling-in work, or for construction purposes, in landfills, is suitable, — the deposit of non-hazardous dredging sludges alongside small waterways from where they have been dredged out and of non-hazardous sludges in surface water including the bed and its subsoil, — the deposit of unpolluted soil or of non-hazardous inert waste resulting from prospecting and extraction, treatment, and storage of mineral resources as well as from the operation of quarries. 30. 10. 98 EN Official Journal of the European Communities C 333/19 3. Without prejudice to Directive 75/442/EEC Member States may declare at their own option, that the deposit of non-hazardous waste, to be defined by the committee established under Article 17 of this Directive, other than inert waste, resulting from prospecting and extraction, treatment and storage of mineral resources as well as from the operation of quarries and which are deposited in a manner preventing environmental pollution or harm to human health, can be exempted from the provisions in Annex I, points 2, 3. 1, 3. 2 and 3. 3 of this Directive. 4. Without prejudice to Directive 75/442/EEC Member States may declare, at their own option, parts or all of Articles 6(d), 7(i), 8(a)(iv), 10, 11(1)(a), (b) and (c), 12(a) and (c), Annex I, points 3 and 4, Annex II (except point 3, level 3, and point 4) and Annex III, points 3 to 5 to this Directive not applicable to: (a) landfill sites for non-hazardous or inert wastes with a total capacity not exceeding 15 000 tonnes or with an annual intake not exceeding 1 000 tonnes serving islands, where this is the only landfill on the island and where this is exclusively destined for the disposal of waste generated on that island. Once the total capacity of that landfill has been used, any new landfill site established on the island shall comply with the requirements of this Directive; (b) landfill sites for non-hazardous or inert waste in isolated settlements if the landfill site is destined for the disposal of waste generated only by that isolated settlement. Not later than two years after the date laid down in Article 18(1), Member States shall notify the Commission of the list of islands and isolated settlements that are exempted. The Commission shall publish the list of islands and isolated settlements. their own option, 5. Without prejudice to Directive 75/442/EEC Member States may declare, at that underground storage as defined in Article 2(f) of this Directive can be exempted from the provisions in Article 13(d) and in Annex I, point 2, except first indent, points 3 to 5, and in Annex III, points 2, 3 and 5 to this Directive. Article 4 Classes of landfill Each landfill shall be classified in one of the following classes: — landfill for hazardous waste, — landfill for non-hazardous waste, — landfill for inert waste. Article 5 Waste and treatment not acceptable in landfills laid down in Article 18(1) and notify 1. Member States shall set up a national strategy for the implementation of the reduction of biodegradable waste going to landfills, not later than two years after the date the Commission of this strategy. This strategy should include measures to achieve the targets set out in paragraph 2 by means of in particular, recycling, composting, biogas production or materials/energy recovery. Within 30 months of the date laid down in Article 18(1) the Commission shall provide the European Parliament and the Council with a report drawing together the national strategies. 2. This strategy shall ensure that: (a) not later than five years after the date laid down in Article 18(1), biodegradable municipal waste going to landfills must be reduced to 75 % of the total amount (by weight) of biodegradable municipal waste produced in 1995 or the latest year before 1995 for which standardised Eurostat data is available; (b) not later than eight years after the date laid down in Article 18(1), biodegradable municipal waste going to landfills must be reduced to 50 % of the total amount (by weight) of biodegradable municipal waste produced in 1995 or the latest year before is 1995 for which standardised Eurostat data available; (c) not later than 15 years after the date laid down in Article 18(1), biodegradable municipal waste going to landfills must be reduced to 35 % of the total amount (by weight) of biodegradable municipal waste produced in 1995 or the latest year before 1995 for which standardised Eurostat data is available. Two years before the date referred to in paragraph (c) the Council shall re-examine the above target, on the basis of a report from the Commission on the practical experience gained by Member States in the pursuance of the targets laid down in paragraphs (a) and (b) accompanied, if appropriate, by a proposal with a view to confirming or amending this target in order to ensure a high level of environmental protection. Member States which, in 1995 or the latest year before 1995 for which standardised Eurostat data is available, put more than 80 % of their collected municipal waste to landfill may postpone the attainment of one or more targets set out in paragraphs (a), (b), or (c) by a period not exceeding four years. Member States intending to C 333/20 EN Official Journal of the European Communities 30. 10. 98 make use of this provision shall inform the Commission of their decision in advance. The Commission shall inform other Member States of these decisions. (b) only hazardous waste that fulfils the criteria set out in accordance with Annex II is assigned to a hazardous landfill; The implementation of the provisions set out in the preceding subparagraph may in no circumstances lead to the attainment of the target set out in paragraph (c) at a date later than four years after the date set out in paragraph (c). (c) landfill for non-hazardous waste may be used for: (i) municipal waste; (ii) non-hazardous waste of any other origin, which fulfil the criteria for the acceptance of waste at landfill for non-hazardous waste set out in accordance with Annex II; 3. Member States shall take measures in order that the following wastes are not accepted in a landfill: (iii) (a) liquid waste; (b) waste which, in the conditions of is explosive, corrosive, oxidising, highly flammable or flammable, as defined in Annex III to Directive 91/689/EEC; landfill, (c) hospital and other clinical wastes arising from medical or veterinary establishments, which are infectious as defined (property H9 in Annex III) by Directive 91/689/EEC and waste falling within category 14 (Annex I. A) of that Directive; (d) whole used tyres from two years from the date laid down in Article 18(1), excluding tyres used as engineering material, and shredded used tyres five years from the date laid down in Article 18(1) (excluding in both instances bicycle tyres and tyres with an outside diameter above 1 400 mm); (e) any other type of waste which does not fulfil the acceptance criteria determined in accordance with Annex II. The dilution or mixture of waste solely in order to 4. meet the waste acceptance criteria is prohibited. Article 6 Waste to be accepted in the different classes of landfill Member States shall take measures in order that: (a) only waste that has been subject to treatment is landfilled. This provision may not apply to inert waste for which treatment is not technically feasible, nor to any other waste for which such treatment does not contribute to the objectives of this Directive, as set out in Article 1, by reducing the quantity of the waste or the hazards to human health or the environment; stable, non-reactive hazardous wastes (e. g. solidified, vitrified), with leaching behaviour equivalent to those of the non-hazardous wastes referred to in point (ii), which fulfil the relevant acceptance criteria set out in accordance with Annex II. These hazardous wastes shall not be deposited in cells destined for biodegradable non-hazardous waste; (d) inert waste landfill sites shall be used only for inert waste. Article 7 Application for a permit Member States shall take measures in order that the application for a landfill permit must contain at least particulars of the following: (a) the identity of the applicant and of the operator when they are different entities; (b) the description of the types and total quantity of waste to be deposited; (c) the proposed capacity of the disposal site; (d) (e) (f) the description of hydrogeological and geological characteristics; including site, the its the proposed methods for pollution prevention and abatement; the proposed operation, monitoring and control plan; (g) the proposed plan for the closure and aftercare procedures; (h) where an impact assessment is required under Council Directive 85/337/EEC of 27 June 1985 on the assessment of the effects of certain public and the private projects on the information provided by the developer in accordance with Article 5 of that Directive; environment (1), (1) OJ L 175, 5. 7. 1985, p. 40. Directive as amended by Directive 97/11/EC (OJ L 73, 14. 3. 1997, p. 5). 30. 10. 98 EN Official Journal of the European Communities C 333/21 (i) the financial security by the applicant, or any other equivalent under Article 8(a)(iv) of this Directive. provision, required as Article 9 Content of the permit Following a successful application for a permit, this information shall be made available to the competent national and Community statistical authorities when requested for statistical purposes. Specifying and supplementing the provisions set out in Article 9 of Directive 75/442/EEC and Article 9 of Directive 96/61/EC, the landfill permit shall state at least the following: Article 8 Conditions of the permit Member States shall take measures in order that: (a) the competent authority does not issue a landfill permit unless it is satisfied that: (i) without prejudice to Article 3(4) and (5), the landfill project complies with all the relevant requirements of this Directive, including the Annexes; (ii) the management of the landfill site will be in the hands of a natural person who is technically competent to manage the site; professional and technical development and training of landfill operators and staff are provided; (iii) the landfill shall be operated in such a manner that the necessary measures are taken to prevent accidents and limit their consequences; (iv) adequate provisions, by way of a financial security or any other equivalent, on the basis of modalities to be decided by Member States, has been or will be made by the applicant prior to the commencement of disposal operations to ensure that the obligations (including aftercare provisions) arising under the permit issued under the provisions of this Directive are discharged and that the closure procedures required by Article 13 are followed. This security or its equivalent shall be kept as long as required by maintenance and aftercare operation of the site in accordance with Article 13(d). Member States may declare, at their own option, that this point does not apply to landfills for inert waste; (b) the landfill project is in line with the relevant waste management plan or plans referred to in Article 7 of Directive 75/442/EEC; (c) prior to the commencement of disposal operations, the competent authority shall inspect the site in order the relevant to ensure conditions of the permit. This will not reduce in any way the responsibility of the operator under the conditions of the permit. it complies with that (a) the class of the landfill; (b) (c) (d) the list of defined types and the total quantity of waste which are authorised to be deposited in the landfill; requirements for the landfill preparations, landfilling operations and monitoring and control procedures, including contingency plans (Annex III, point 4. B), as well as provisional requirements for the closure and aftercare operations; the obligation on the applicant to report at least annually to the competent authority on the types and quantities of waste disposed of and on the results of the monitoring programme as required in Articles 12 and 13 and Annex III. Article 10 Cost of the landfill of waste Member States shall take measures to ensure that all of the costs involved in the setting up and operation of a landfill site, including as far as possible the cost of the financial security or in Article 8(a)(iv), and the estimated costs of the closure and aftercare of the site for a period of at least 30 years shall be covered by the price to be charged by the operator for the disposal of any type of waste in that site. Member States shall ensure the collection of any necessary cost information. its equivalent referred to Article 11 Waste acceptance procedures 1. Member States shall take measures in order that prior to accepting the waste at the landfill site: (a) before or at the time of delivery, or of the first in a series of deliveries, provided the type of waste remains unchanged, the holder or the operator can show, by means of the appropriate documentation, that the waste in question can be accepted at that site according to the conditions set in the permit, and that it fulfils the acceptance criteria set out in Annex II; C 333/22 EN Official Journal of the European Communities 30. 10. 98 (b) the following reception procedures are respected by the operator: such exempted sites forms part of the regular reports to the Commission on the implementation of the Directive. — checking of the waste documentation, including those documents required by Article 5(3) of Directive 91/689/EEC and, where they apply, those required by Council Regulation (EEC) No 259/93 of 1 February 1993 on the supervision and control of shipments of waste within, the European Community (1), into and out of — visual inspection of the waste at the entrance and at the point of deposit and, as appropriate, verification of conformity with the description provided in the documentation submitted by the holder. If representative samples have to be taken in order to implement Annex II, point 3, level 3, the results of the analyses shall be kept and the in conformity with sampling shall be made Annex II, point 5. These samples shall be kept at least one month, — keeping a register of the quantities and characteristics of the waste deposited, indicating origin, date of delivery, identity of the producer or collector in the case of municipal waste, and, in the case of hazardous waste, the precise location on the site. This information shall be made available to the competent national and Community statistical authorities when requested for statistical purposes; (c) the operator of the landfill shall always provide written acknowledgement of receipt of each delivery accepted on the site; (d) without prejudice to the provisions of Regulation (EEC) No 259/93, if waste is not accepted at a landfill the operator shall notify without delay the competent authority of the non-acceptance of the waste. 2. For landfill sites which have been exempted from provisions of this Directive by virtue of Article 3(4) and (5), Member States shall take the necessary measures to provide for: — regular visual inspection of the waste at the point of deposit in order to ensure that only non-hazardous waste from the island or the isolated settlement is accepted at the site; and Article 12 Control and monitoring procedures in the operational phase Member States shall take measures in order that control and monitoring procedures in the operational phase meet at least the following requirements: (a) (b) the operator of a landfill shall carry out during the operational phase a control and monitoring programme as specified in Annex III; the operator shall notify the competent authority of any significant adverse environmental effects revealed by the control and monitoring procedures and follow the decision of the competent authority on the nature and timing of the corrective measures to be taken. These measures shall be undertaken at the expense of the operator. At a frequency to be determined by the competent authority, and in any event at least once a year, the operator shall report, on the basis of aggregated data, all monitoring results the competent to the purpose of demonstrating for authorities compliance with permit conditions and increasing the knowledge on waste behaviour in the landfills; (c) the quality control of the analytical operations of the control and monitoring procedures and/or of the analyses referred to in Article 11(1)(b) are carried out by competent laboratories. Article 13 Closure and aftercare procedures Member States shall take measures in order that, in accordance, where appropriate, with the permit: (a) a landfill or part of it shall start the closure — a register on the quantities of waste that are deposited procedure: at the site be kept. Member States shall ensure that information on the quantities and, where possible, the type of waste going to (i) when the relevant conditions stated in the permit are met, or (ii) under the authorisation of the competent authority, at the request of the operator, or (1) OJ L 30, 6. 2. 1993, p. 1. Regulation as amended by Regulation (EC) No 120/97 (OJ L 22, 24. 1. 1997, p. 14). (iii) by reasoned decision of the competent authority; 30. 10. 98 EN Official Journal of the European Communities C 333/23 (b) a landfill or part of it may only be considered as definitely closed after the competent authority has carried out a final on-site inspection, has assessed all the reports submitted by the operator and has communicated to the operator its approval for the closure. This shall not in any way reduce the responsibility of the operator under the conditions of the permit; (c) on the basis of the approved site-conditioning plan, the competent authority shall authorise the necessary work and shall lay down a transitional period for the completion of the plan. Any existing landfill shall comply with the requirements of this Directive with the exception of the requirements in Annex I, point 1 within eight years after the date laid down in Article 18(1); (c) after a landfill has been definitely closed, the operator shall be responsible for its maintenance, monitoring and control in the aftercare phase for as long as may be required by the competent authority, taking into account the time during which the landfill could present hazards. The operator shall notify the competent authority of any significant adverse environmental effects revealed by the control procedures and shall follow the decision of the competent authority on the nature and timing of the corrective measures to be taken; (d) is landfill for as long as the competent authority considers that likely to cause a hazard to the a environment, the operator of the site shall be responsible for monitoring and analysing landfill gas and leachate from the site and the groundwater regime in the vicinity of the site in accordance with Annex III. Article 14 Existing landfill sites Member States shall take measures in order that landfills which have been granted a permit, or which are already in operation at the time of transposition of this Directive, may not continue to operate unless the steps outlined below are accomplished as soon as possible and within eight years after the date laid down in Article 18(1) at the latest: (a) within a period of one year after the date laid down in Article 18(1), the operator of a landfill shall prepare and present to the competent authorities, for their approval, a conditioning plan for the site including the particulars listed in Article 8 and any corrective measures which the operator considers in order to comply with the will be needed requirements of this Directive with the exception of the requirements in Annex I, point 1; (b) following the presentation of the conditioning plan, the competent authorities shall take a definite decision on whether operations may continue on the basis of the said conditioning plan and this Directive. Member States shall take the necessary measures to close down as soon as possible, in accordance with Articles 7(g) and 13, sites which have not been granted, in accordance with Article 8, a permit to continue to operate; (d) (i) within one year after the date laid down in Article 18(1), Articles 4, 5, and 11 and Annex II shall apply to landfills for hazardous waste; (ii) within three years after the date laid down in Article 18(1), Article 6 shall apply to landfills for hazardous waste. Article 15 Obligation to report At intervals of three years Member States shall send to the Commission a report on the implementation of this Directive, paying particular attention to the national strategies to be set up in pursuance of Article 5. The report shall be drawn up on the basis of a questionnaire or outline drafted by the Commission in accordance with the procedure laid down in Article 6 of Directive 91/692/EEC (1). The questionnaire or outline shall be sent to Member States six months before the start of the period covered by the report. The report shall be sent to the Commission within nine months of the end of the three-year period covered by it. The Commission shall publish a Community report on the implementation of this Directive within nine months of receiving the reports from the Member States. Article 16 Committee Any amendments necessary for adapting the Annexes to this Directive to scientific and technical progress and any proposals for the standardisation of control, sampling and analysis methods in relation to the landfill of waste shall be adopted by the Commission, assisted by the committee established by Article 18 of Directive 75/442/EEC and in accordance with the procedure set out in Article 17 of this Directive. Any amendments to the Annexes shall only be made in line with the principles laid down in this Directive as expressed in the Annexes. To this end, as regards Annex II, the following shall be observed by the committee: taking into account the (1) OJ L 377, 31. 12. 1991, p. 48. C 333/24 EN Official Journal of the European Communities 30. 10. 98 general principles and general procedures for testing and acceptance criteria as set out in Annex II, specific criteria and/or test methods and associated limit values should be set for each class of landfill, including if necessary specific types of landfill within each class, including underground storage. Proposals for the standardisation of control, sampling and analysis methods in relation to the Annexes of this Directive shall be adopted by the Commission, assisted by the committee, within two years after the entry into force of this Directive. for the The Commission, assisted by the committee, will adopt regular provisions transmission of the statistical date referred to in Articles 5, 7 and 11 of this Directive, within two years after the entry into force of this Directive, and for the amendments of such provisions when necessary. harmonisation and Article 17 Committee procedure Council a proposal relating to the measures to be taken. The Council shall act by a qualified majority. If on the expiry of a period of three months from the date of referral to the Council, the Council has not acted, the the proposed measures shall be adopted by Commission. Article 18 Transposition 1. Member States shall bring into force the laws, regulations and administrative provisions necessary to comply with this Directive not later than two years after its entry into force. They shall forthwith inform the Commission thereof. When Member States adopt these measures, they shall contain a reference to this Directive or shall be accompanied by such reference on the occasion of their official publication. The methods of making such a reference shall be laid down by Member States. The Commission shall be assisted by a committee composed of the representatives of the Member States and chaired by the representative of the Commission. 2. Member States shall communicate the texts of the provisions of national law which they adopt in the field covered by this Directive to the Commission. The representative of the Commission shall submit to the committee a draft of the measures to be taken. The committee shall deliver its opinion on the draft within a time limit which the chairman may lay down according to the urgency of the matter. The opinion shall be delivered by the majority laid down in Article 148(2) of the Treaty in the case of decisions which the Council is required to adopt on a proposal from the Commission. The votes of the representatives of the Member States within the Committee shall be weighted in the manner set out in that Article. The chairman shall not vote. The Commission shall adopt the measures envisaged if they are the committee. in accordance with the opinion of Article 19 Entry into force This Directive will enter into force on the day of its publication in the Official Journal of the European Communities. Article 20 Addressees This Directive is addressed to the Member States. Done at. If the measures envisaged are not in accordance with the opinion of the committee, or if no opinion is delivered, the Commission shall, without delay, submit to the For the Council The President 30. 10. 98 EN Official Journal of the European Communities C 333/25 ANNEX I GENERAL REQUIREMENTS FOR ALL CLASSES OF LANDFILLS 1. Location 1. 1. The location of a landfill must take into consideration requirements relating to: (a) the distances from the boundary of the site to residential and recreation areas, waterways, water bodies and other agricultural or urban sites; (b) the existence of groundwater, coastal water or nature protection zones in the area; (c) the geological and hydrogeological conditions in the area; (d) the risk of flooding, subsidence, landslides or avalanches on the site; (e) the protection of the natural or cultural patrimony in the area. 1. 2. The landfill can be authorised only if the characteristics of the site with respect to the abovementioned requirements, or the corrective measures to be taken, indicate that the landfill does not pose a serious environmental risk. 2. Water control and leachate management Appropriate measures shall be taken, with respect to the characteristics of the landfill and the meteorological conditions, in order to: — control water from precipitations entering into the landfill body, — prevent surface water and/or groundwater from entering into the landfilled waste, — collect contaminated water and leachate. If an assessment based on cnsideration of the location of the landfill and the waste to be accepted shows that the landfill poses no potential hazard to the environment, the competent authority may decide that this provision does not apply, — treat contaminated water and leachate collected from the landfill to the appropriate standard required for their discharge. The above provisions may not apply to landfills for inert waste. 3. Protection of soil and water 3. 1. A landfill must be situated and designed so as to meet the necessary conditions for proventing pollution of the soil, groundwater of surface water and ensuring efficient collection of leachate as and when required according to section 2. Protection of soil, groundwater and surface water is to be achieved by the combination of a geological barrier and a bottom liner during the operational/active phase and by the combination of a geological barrier and a top liner during the passive phase/post closure. 3. 2. The geological barrier is determined by geological and hydrogeological conditions below and in the vicinity of a landfill site providing sufficient attenuation capacity to prevent a potential risk to soil and groundwater. The landfill base and sides shall consist of a mineral layer which satisfies permeability and thickness requirements with a combined effect in terms of protection of soil, groundwater and surface water at least equivalent to the one resulting from the following requirements: — landfill for hazardous waste: K # 1,0 × 10−9 m/s; thickness $ 5 m — landfill for non-hazardous waste: K # 1,0 × 10−9 m/s; thickness $ 1 m C 333/26 EN Official Journal of the European Communities 30. 10. 98 — landfill for inert waste: K # 1,0 × 10−7 m/s; thickness $ 1 m m/s = meter/second Where the geological barrier does not naturally meet the above conditions it can be completed aftificially and reinforced by other means giving equivalent protection. An artificially established geological barrier should be no less than 0,5 metres thick. 3. 3. In addition to the geological barrier described above a leachate collection and sealing system must be added in accordance with the following principles so as to ensure that leachate accumulation at the base of the landfill is kept to a minimum: Leachate collection and bottom sealing Landfill category Non hazardous Hazardous Artificial sealing liner Drainage layer $ 0,5 m Required Required Required Required Member States may set general or specific requirements for inert waste landfills and for the characteristics of the abovementioned technical means. If the competent authority after a consideration of the potential hazards to the environment finds that the prevention of is necessary, a surface sealing may be prescribed. Recommendations for the surface sealing are as follows: leachate formation Landfill category Non hazardous Hazardous Gas drainage layer Artificial sealing liner Impermeable mineral layer Drainage layer. 0,5 m Topsoil cover. 1 m Required Not required Not required Required Required Required Required Required Required Required 3. 4. If, on the basis of an assessment of environmental risks taking into account, in particular, Directive 80/68/EEC (1), the competent authority has decided, in accordance with section 2 (Water control and leachate management), that collection and treatment of leachate is not necessary or it has been established that the landfill poses no potential hazard to soil, groundwater or surface water, the requirements in paragraphs 3. 2 and 3. 3 may be reduced accordingly. In the case of landfills for inert waste these requirements may be adapted by national legislation. 3. 5. The method to be used for the determination of the permeability coefficient for landfills, in the field and for the whole extension of the site, is to be developed and approved by the committee set up under Article 17 of this Directive. 4. Gas control 4. 1. Appropriate measures shall be taken in order to control the accumulation and migration of landfill gas (Annex III). 4. 2. Landfill gas shall be collected from all landfills receiving biodegradable waste and the landfill gas must be treated and used. If the gas collected cannot be used to produce energy, it must be flared. 4. 3. The collection, treatment and use of landfill gas under paragraph 4. 2 shall be carried on in a manner which minimises damage to or deterioration of the environment and risk to human health. (1) OJ L 20, 26. 1. 1980, p. 43. Directive as last amended by Directive 91/692/EEC (OJ L 377, 31. 12. 1991, p. 48). 30. 10. 98 EN Official Journal of the European Communities C 333/27 5. Nuisances and hazards Measures shall be taken to minimise nuisances and hazards arising from the landfill through: — emissions of odours and dust, — wind-blown materials, — noise and traffic, — birds, vermin and insects, — formation of aerosols, — fires. The landfill shall be equipped so that dirt originating from the site is not dispersed onto public roads and the surrounding land. 6. Stability The emplacement of waste on the site shall take place in such a way as to ensure stability of the mass of waste and associated structures, particularly in respect of avoidance of slippages. Where an artificial barrier is established it must be ascertained that the geological substratum, considering the morphology of the landfill, is sufficiently stable to prevent settlement that may cause damage to the barrier. 7. Barriers The landfill shall be secured to prevent free access to the site. The gates shall be locked outside operating hours. The system of control and access to each facility should contain a programme of measures to detect and discourage illegal dumping in the facility. C 333/28 EN Official Journal of the European Communities 30. 10. 98 ANNEX II WASTE ACCEPTANCE CRITERIA AND PROCEDURES 1. Introduction This Annex describes: — general principles for acceptance of waste at the various classes of landfills. The future waste classification procedure should be based on these principles, — guidelines outlining preliminary waste acceptance procedures to be followed until a uniform waste classification and acceptance procedure has been developed. This procedure will, together with the relevant sampling procedures, be developed by the technical committee referred to in Article 16 of this Directive. The technical committee shall develop criteria which have to be fulfilled for certain hazardous waste to be accepted in landfills for non-hazardous waste. These criteria should, in particular, take into account the short-, medium- and long-term leaching behaviour of such waste. These criteria shall be developed within two years of the entry into force of this Directive. The technical committee shall also develop criteria which have to be fulfilled for waste to be accepted in underground storage. These criteria must take into account, in particular, that the waste is not to be expected to react with each other and with the rock. This work by the technical committee, with the exception of proposals for the standardisation of control, sampling and analysis methods in relation to the Annexes of this Directive which shall be adopted within two years after the entry into force of this Directive, shall be completed within three years from the entry into force of this Directive and must be carried out having regard to the objectives set forth in Article 1 of this Directive. 2. General principles The composition, leachability, long-term behaviour and general properties of a waste to be landfilled must be known as precisely as possible. Waste acceptance at a landfill can be based either on lists of accepted or refused waste, defined by nature and origin, and on waste analysis methods and limit values for the properties of the waste to be accepted. The future waste acceptance procedures described in this Directive shall as far as possible be based on standardised waste analysis methods and limit values for the properties of waste to be accepted. Before the definition of such analysis methods and limit values, Member States should at least set national lists of waste to be accepted or refused at each class of landfill, or define the criteria required to be on the lists. In order to be accepted at a particular class of landfill, a type of waste must be on the relevant national list or fulfil criteria similar to those required to be on the list. These lists, or the equivalent criteria, and the analysis methods and limit values shall be sent to the Commission within six months of the transposition of this Directive or whenever they are adopted at national level. These lists or acceptance criteria should be used to establish site-specific lists, i. e. the list of accepted waste specified in the permit in accordance with Article 9 of this Directive. The criteria for acceptance of waste on the reference lists or at a class of landfill may be based on other legislation and/or on waste properties. Criteria for acceptance at a specific class of landfill must be derived from considerations pertaining to: — protection of the surrounding environment (in particular groundwater and surface water), — protection of the environmental protection systems (e. g. liners and leachate treatment systems), — protection of the desired waste-stabilisation processes within the landfill, — protection against human-health hazards. 30. 10. 98 EN Official Journal of the European Communities C 333/29 Examples of waste property-based criteria are: — requirements on knowledge of total composition, — limitations on the amount of organic matter in the waste, — requirements or limitations on the biodegradability of the organic waste components, — limitations on the amount of specified, potentially harmful/hazardous components (in relation to the abovementioned protection criteria), — limitations on the potential and expected leachability of specified, potentially harmful/hazardous components (in relation to the abovementioned protection criteria), — ecotoxicological properties of the waste and the resulting leachate. The property-based criteria for acceptance of waste must generally be most extensive for inert waste landfills and can be less extensive for non-hazardous waste landfills and least extensive for hazardous waste landfills owing to the higher environmental protection level of the latter two. 3. General procedures for testing and acceptance of waste The general characterisation and testing of waste must be based on the following three level hierarchy: Level 1: Basic characterisation. This constitutes a thorough determination, according to standardised analysis and behaviour-testing methods, of the short- and long-term leaching behaviour and/or characteristic properties of the waste. Level 2: Compliance testing. This constitutes periodical testing by similar standardised analysis and behaviour-testing methods to determine whether a waste complies with permit conditions and/or specific reference criteria. The tests focus on key variables and behaviour identified by basic characterisation. Level 3: On-site verification. This constitutes rapid check methods to confirm that a waste is the same as that which has been subjected to compliance testing and that which is described in the accompanying documents. It may merely consist of a visual inspection of a load of waste before and after unloading at the landfill site. A particular type of waste must normally be characterised at level 1 and pass the appropriate criteria in order to be accepted on a reference list. In order to remain on a site-specific list, a particular type of waste must at regular intervals (e. g. annually) be tested at level 2 and pass the appropriate criteria. Each waste load arriving at the gate of a landfill must be subjected to level 3 verification. Certain waste types may be exempted permanently or temporarily from testing at level 1. This may be due to impracticability of testing, to unavailability of appropriate testing procedures and acceptance criteria or to overriding legislation. 4. Guidelines for preliminary waste acceptance procedures Until this Annex is fully completed only level-3 testing is mandatory and level 1 and level 2 applied to the extent possible. At this preliminary stage waste to be accepted at a particular class of landfill must either be on a restrictive national or site-specific list for that class of landfill or fulfil criteria similar to those required to get on the list. The following general guidelines may be used to set preliminary criteria for acceptance of waste at the three major classes of landfill or the corresponding lists: — inert waste landfills: only inert waste as defined in Article 2(e) can be accepted on the list, C 333/30 EN Official Journal of the European Communities 30. 10. 98 — non-hazardous waste landfills: in order to be accepted on the list a waste type must not be covered by Directive 91/689/EEC, — hazardous waste landfills: a preliminary rough list for hazardous waste landfills would consist of only those waste types covered by Directive 91/689/EEC. Such waste types should, however, not be accepted on the list without prior treatment if they exhibit total contents or leachability of potentially hazardous components that are high enough to constitute a short-term occupational or environmental risk or to prevent sufficient waste stabilisation within the projected lifetime of the landfill. 5. Sampling of waste Sampling of waste may pose serious problems with respect to representation and techniques owing to the heterogeneous nature of many wastes. A European standard for sampling of waste will be developed. Until this standard is approved by Member States in accordance with Article 17 of this Directive, the Member States may apply national standards and procedures. 30. 10. 98 EN Official Journal of the European Communities C 333/31 ANNEX III CONTROL AND MONITORING PROCEDURES IN OPERATION AND AFTER-CARE PHASES 1. Introduction The purpose of this Annex is to provide the minimum procedures for monitoring to be carried out to check: — that waste has been accepted for disposal in accordance with the criteria set for the category of landfill in question: — that the processes within the landfill proceed as desired, — that the environmental protection systems are functioning fully as intended, — that the permit conditions for the landfill are fulfilled. 2. Meteorological data Under their reporting obligation (Article 15), Member States should supply data on the collection method for meteorological data. It is up to Member States to decide how the data should be collected (in situ, national meteorological network, etc. ). Should Member States decide that water balances are an effective tool for evaluating whether leachate is building up in the landfill body or whether the site is leaking, it is recommended that the following data are collected from monitoring at the landfill or from the nearest meteorological station, as long as required by the competent authority in accordance with Article 13(c) of this Directive: Operation phase Aftercare phase Daily Daily Daily Daily Daily Daily, added to monthly values Monthly average Not required Daily, added to monthly values Monthly average 1. 1. Volume of precipitation 1. 2. Temperature (min. , max. , 14. 00 CET) 1. 3. Direction and force of prevailing wind 1. 4. Evaporation (lysimeter) (1) 1. 5. Atmospheric humidity (14. 00 CET) (1) Or through other suitable methods. 3. Emission data: water, leachate and gas control Sampling of leachate and surface water if present must be collected at representative points. Sampling and measuring (volume and composition) of leachate must be performed separately at each point at which leachate is discharged from the site. Reference: general guidelines on sampling technology, ISO 5667-2 (1991). Monitoring of surface water if present shall be carried out at not less than two points, one upstream from the landfill and one downstream. Gas monitoring must be representative for each section of the landfill. The frequency of sampling and analysis is listed in the following table. C 333/32 EN Official Journal of the European Communities 30. 10. 98 For leachate and water, a sample, representative of the average composition, shall be taken for monitoring. 2. 1. Leachate volume 2. 2. Leachate composition (2) 2. 3. Volume and composition of surface water (7) 2. 4. Potential gas emissions and atmospheric pressure (4) (CH4, CO2, O2, H2S, H2 etc. ) Operating phase Aftercare phase (3) Monthly (1) (3) Every six months Quarterly (3) Quarterly (3) Every six months Every six months Monthly (3) (5) Every six months (6) (1) The frequency of sampling could be adapted on the basis of the morphology of the landfill waste (in tumulus, buried, etc). This has to be specified in the permit. (2) The parameters to be measured and the substances to be analysed vary according to the composition of the waste deposited; they must be laid down in the permit document and reflect the leaching characteristics of the wastes. (3) If the evaluation of data indicates that longer intervals are equally effective, they may be adapted. For leachates, conductivity must always be measured at least once a year. (4) These measurements are related mainly to the content of organic material in the waste. (5) CH4, CO2, O2, regularly, other gases as required, according to the composition of the waste deposited, with a view to reflecting its leaching properties. (6) Efficiency of the gas extraction system must be checked regularly. (7) On the basis of the characteristics of the landfill site, the competent authority may determine that these measurements are not required, and will report accordingly in the way laid down in Article 15 of the Directive. 2. 1 and 2. 2 apply only where leachate collection takes place (see Annex I(2)). 4. Protection of groundwater A. SAMPLING The measurements must be such as to provide information on groundwater likely to be affected by the discharging of waste, with at least one measuring point in the groundwater inflow region and two in the outflow region. This number can be increased on the basis of a specific hydrogeological survey and the need for an early identification of accidental leachate release in the groundwater. Sampling must be carried out in at least three locations before the filling operations in order to establish reference values for future sampling. Reference Sampling groundwaters, ISO 5667, Part 11, 1993. B. MONITORING The parameters to be analysed in the samples taken must be derived from the expected composition of the leachate and the groundwater quality in the area. In selecting the parameters for analysis, account should be taken of mobility in the groundwater zone. Parameters could include indicator parameters in order to ensure an early recognition of change in water quality (1). Level of groundwater Groundwater composition Operation phase Aftercare phase Every six months (1) Every six months (1) Site-specific frequency (2) (3) Site-specific frequency (2) (3) (1) If there are fluctuating groundwater levels, the frequency must be increased. (2) The frequency must be based on possibility for remedial actions between two samplings if a trigger level is reached, i. e. the frequency must be determined on the basis of knowledge and the evaluation of the velocity of groundwater flow. (3) When a trigger level is reached (see C), verification is necessary by repeating the sampling. When the level has been confirmed, a contingency plan (laid down in the permit) must be followed. C. TRIGGER LEVELS Significant adverse environmental effects, as referred to in Articles 12 and 13 of this Directive, should be considered to have occurred in the case of groundwater, when an analysis of a groundwater (1) Recommended parameters: pH, TOC, phenols, heavy metals, fluoride, AS, oil/hydrocarbons. 30. 10. 98 EN Official Journal of the European Communities C 333/33 sample shows a significant change in water quality. A trigger level must be determined taking account of the specific hydrogeological formations in the location of the landfill and groundwater quality. The trigger level must be laid down in the permit whenever possible. The observations must be evaluated by means of control charts with established control rules and levels for each downgradient well. The control levels must be determined from local variations in groundwater quality. 5. Topography of the site: data on the landfill body Operating phase After-care phase 5. 1. Structure and composition of landfill body (1) Yearly 5. 2. Settling behaviour of the level of the landfill Yearly Yearly reading body (1) Data for the status plan of the concerned landfill: surface occupied by waste, volume and composition of waste, methods of depositing, time and duration of depositing, calculation of the remaining capacity still available at the landfill. C 333/34 EN Official Journal of the European Communities 30. 10. 98 STATEMENT OF THE COUNCIL’S REASONS I. INTRODUCTION 1. On 14 March 1997 the Commission submitted a proposal for a Directive (1), based on Article 130s(1), on the landfill of waste. 2. The European Parliament delivered its opinion on 19 February 1998 (2) at a first reading, proposing 29 amendments. Following receipt of that opinion the Commission submitted an amended proposal (3) on 26 March 1998. The Economic and Social Committee delivered its opinion on 1 October 1997. 3. On 4 June 1998 the Council adopted its Common Position in accordance with Article 189c of the Treaty. II. PURPOSE 4. With the aim of preventing or reducing as far as possible negative effects on the environment from landfilling of waste, as well as any resulting risks to human health, during the whole life cycle of the landfill, this proposal establishes in the form of a framework Directive and on the basis of a classification of waste and of landfills for hazardous, non-hazardous and inert wastes, — the procedures for issuing a permit for the acceptance of waste at a landfill, the control and monitoring procedures in the operational phase and the closure procedure, — the technical conditions to be met by sites and facilities which are to serve as landfills, and the waste to be accepted in the different classes of landfill, — the authorisation procedures for the opening of a landfill, — the targets to be achieved by national strategies for the implementation of the reduction of biodegradable municipal waste going to landfills. III. ANALYSIS OF THE COMMON POSITION General comments 5. In view of the above objective, aware of the part played by local, natural conditions in the establishment and operation of landfills and taking into consideration particular conditions prevailing in Member States as regards their production of waste and their current waste disposal practices, the Council has endeavoured to retain the provisions which guarantee a high level of health and environmental protection without seeking to ineffective or even impose systematic harmonisation, which would have been inapplicable. In compliance with the principle of subsidiarity and in the light of the above consideration, the provisions adopted essentially resulted in amendment of the Commission proposal to improve comprehensibility and flexibility. These changes relate chiefly to the scope, the strategy for the reduction of biodegradable waste going to landfills, and the timetable for existing landfills. 6. On the basis of the above guidelines the Council was able to include — verbatim, in substance or in part: (1) OJ C 156, 24. 5. 1997, p. 10. (2) OJ C 80, 16. 3. 1998, p. 204. (3) OJ C 126, 24. 4. 1998, p. 11. 30. 10. 98 EN Official Journal of the European Communities C 333/35 — the European Parliament amendments the Commission had incorporated into its amended proposal, with the exception of amendments 1, 6, 10, 11, 19, 21, 24, 26 and 29, — amendments 2, 3, 7, 12 and 31, which the Commission had not incorporated in its amended proposal. Specific comments (The references below relate, save where otherwise indicated, to the text of the amended proposal. References to the common position are given in bold type. ) The main modifications made by the Council to the Commission’s amended proposal are the following: (i) Article 1 Instead of listing all the different phases in the life cycle of a landfill the Council found it more satisfactory to refer, in this general Article, to the ‘whole life cycle of the landfill’. Given the similarity of the overall objective of this Directive to that of Directive 96/61/EC (the IPPC Directive) the Council considered it useful to clarify their mutual relationship in the second paragraph of Article 1. Accordingly the second sentence of Article 3(1) has been deleted. (ii) Article 2 In Article 2(b), the words ‘commercial, industrial, institutional and. ’ have been deleted, since the origin of waste is not decisive in the structure of the Directive. The definition of hazardous waste (paragraph (c)) has been made more consistent by referring directly to the basis provision in Community law, i. e. Article 1(4) of Directive 91/689/EEC. Definitions (f) and (g): in order to bring clarity when reflecting the substance of amendments 10 and 12 and in the light of their differentiated treatment under Article 3, the Council was of the view that a distinction should be made between ‘landfill’ (g) and ‘underground storage’ (f). Furthermore, to take into account certain recovery and treatment processes, it was deemed appropriate to extend to three years the period of storage prior to recovery or treatment. Definition (h) (treatment) includes ‘thermal processes’ as distinct from ‘physical processes’. Definition (q) (liquid waste): as it did not appear feasible to base a definition of liquid waste on their content of solid matter the Council has retained the definition originally proposed by the Commission. Definition (r) (isolated settlement) has been made more specific by referring to the meteorological conditions which affect these settlements. (iii) Article 3 While the deposit of non-hazardous inert waste resulting from mining activities or the operation of quarries are entirely excluded from the scope of the Directive (paragraph 2, fourth indent) the Council was of the view that non-hazardous non-inert waste resulting from mining activities or the operation of quarries can be exempted only from certain provisions (paragraph 3). In the same way, only limited exemptions reflecting the characteristics of underground storages may be granted to these sites (paragraph 4). Although the total capacity under which a site for non-hazardous or inert waste may be exempted from certain provisions has been raised from 10 000 to 15 000 tonnes (paragraph 4(a)), it has been clarified that these exemptions apply only to existing landfills. C 333/36 EN Official Journal of the European Communities 30. 10. 98 (iv) Article 5 Although broadly supportive of the approach advocated by the Commission as regards the reduction of biodegradable waste going to landfills the Council felt that the strategies to be set up by Member States to that effect should not be limited to municipal waste but cover all biodegradable waste (paragraph 1) and that the first target for biodegradable municipal waste shall be mandatory (paragraph 2(a)). The report on national strategies shall be presented within 30 months of the date of transposition of the Directive, i. e. six months after the setting up of their strategies by Member States (paragraph 1), which is equivalent to the delay foreseen in the amended proposal. As regards subsequent targets the moderately delayed timetable which appears in paragraph 2 could facilitate the development of alternative disposal practices and should enable Member States to achieve these targets. In order to take into account the uncertainties which could affect the third target, a review clause has been inserted. (v) Article 6 Paragraph (c)(iii) foresees that waste, which following appropriate treatment is stable and non-reactive, i. e. no longer exhibits hazardous properties, and which fulfils specific acceptance criteria, may be deposited in landfill for non-hazardous waste. (vi) Article 8 A provision relating to the prevention of accidents has been inserted (paragraph (a)(iii)). Given their intrinsic low risk, landfills for inert waste may be exempted from the requirement on financial security (paragraph (a)(iv)). (vii) Article 10 Given the uncertainty affecting the determination of the cost of the financial security or its equivalent and because of the various ways in which a landfill can be administered it is only possible to try to include as far as possible this cost in the price to be charged at a landfill. (viii) Article 11 Given the nature of the sites (isolated settlement etc. ) covered by the register and the fact that there is already an obligation of reporting on these sites on a national basis, the added-value of having each register accessible to the public is doubtful. (ix) Article 13 Amendment 24 has not been retained as it does not add anything to the ability of competent authorities to set the period during which the operator shall be responsible for the monitoring of the landfill. (x) Articles 14 and 18 It seemed unrealistic, given administrative practices, the technical delays involved in the conditioning of existing sites and the redirecting of waste following the closure of a landfill, to prescribe an overall time-limit of five years and to specify intermediate deadlines. The Council thought it was more realistic to adopt a maximum total time limit of 10 years after entry into force of the Directive (introductory passage to Article 14) while setting a closer deadline for landfill for hazardous waste (one year after transposition, Article 14(d)) for the implementation of certain provisions. Amendment 26 has not been retained as it does not add anything to existing obligations under Directive 75/442/EEC. 30. 10. 98 EN Official Journal of the European Communities C 333/37 The same assessment of the inevitable administrative delay involved in transposing such a technical Directive led the Council to opt for a transposition period of two years (Article 18(1)). (xi) Article 15 The reporting obligation (Article 15) reflects, inter alia, amendment 7 according to which Member States must report on the implementation of Article 5. This obligation is also mentioned in recital 34. (xii) Annexes Annex I: — given the diversity of local conditions it does not seem appropriate to impose a uniform minimum distance between landfills and residential sites; this requirement has therefore not been retained in section 1. 1 paragraph (a), — the reference to the framework Directive on water has been omitted as this Directive is not yet adopted. Annex II: Its introduction has been expanded in order to list the various acceptance criteria which the technical committee will have to establish. (xiii) Preamble Given that a recital on the Council resolution of 1996 and related recitals are already included in the preamble, it does not seem appropriate to include, out of context, a recital on the hierarchy of waste management. Recital 4 reflects the substance of amendments 2, 3 and 5