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Document 01999L0031-20180704
Council Directive 1999/31/EC of 26 April 1999 on the landfill of waste
Consolidated text: Council Directive 1999/31/EC of 26 April 1999 on the landfill of waste
Council Directive 1999/31/EC of 26 April 1999 on the landfill of waste
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01999L0031 — EN — 04.07.2018 — 004.001
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COUNCIL DIRECTIVE 1999/31/EC of 26 April 1999 (OJ L 182 16.7.1999, p. 1) |
Amended by:
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Official Journal |
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page |
date |
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REGULATION (EC) No 1882/2003 OF THE EUROPEAN PARLIAMENT AND OF THE COUNCIL of 29 September 2003 |
L 284 |
1 |
31.10.2003 |
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REGULATION (EC) No 1137/2008 OF THE EUROPEAN PARLIAMENT AND OF THE COUNCIL of 22 October 2008 |
L 311 |
1 |
21.11.2008 |
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L 328 |
49 |
10.12.2011 |
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DIRECTIVE (EU) 2018/850 OF THE EUROPEAN PARLIAMENT AND OF THE COUNCIL of 30 May 2018 |
L 150 |
100 |
14.6.2018 |
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COUNCIL DIRECTIVE 1999/31/EC
of 26 April 1999
on the landfill of waste
Article 1
Overall objective
Article 2
Definitions
For the purposes of this Directive:
the definitions of ‘waste’, ‘hazardous waste’, ‘non-hazardous waste’, ‘municipal waste’, ‘waste producer’, ‘waste holder’, ‘waste management’, ‘separate collection’, ‘recovery’, ‘preparing for re-use’, ‘recycling’ and ‘disposal’ laid down in Article 3 of Directive 2008/98/EC shall apply;
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‘inert waste’ means waste that does not undergo any significant physical, chemical or biological transformations. Inert waste will not dissolve, burn or otherwise physically or chemically react, 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;
‘underground storage’ means a permanent waste storage facility in a deep geological cavity such as a salt or potassium mine;
‘landfill’ means a waste disposal site for the deposit of the waste onto or into land (i.e. underground), including:
but excluding:
‘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;
‘leachate’ means any liquid percolating through the deposited waste and emitted from or contained within a landfill;
‘landfill gas’ means all the gases generated from the landfilled waste;
‘eluate’ means the solution obtained by a laboratory leaching test;
‘operator’ means the natural or 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 after-care phase;
‘biodegradable waste’ means any waste that is capable of undergoing anaerobic or aerobic decomposition, such as food and garden waste, and paper and paperboard;
▼M4 —————
‘applicant’ means any person who applies for a landfill permit under this Directive;
‘competent authority’ means that authority which the Member States designate as responsible for performing the duties arising from this Directive;
‘liquid waste’ means any waste in liquid form including waste waters but excluding sludge;
‘isolated settlement’ means a settlement:
In outermost regions within the meaning of Article 349 of the Treaty, Member States may decide to apply the following definition:
‘isolated settlement’ means a settlement:
Article 3
Scope
Without prejudice to existing Community legislation, the following shall be excluded from the scope of this Directive:
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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:
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;
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.
Article 4
Classes of landfill
Each landfill shall be classified in one of the following classes:
Article 5
Waste and treatment not acceptable in landfills
This strategy shall ensure that:
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
not later than eight years afte 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 1995 for which stadardised Eurostat data is available;
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 lates year before 1995 for which standardised Eurostat data is available.
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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 the targets set out in paragraphs (a), (b), or (c) by a period not exceeding four years. Member States intending to make use of this provision shall inform in advance the Commission of their decision. The Commission shall inform other Member States and the European Parliament of these decisions.
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).
Member States shall take measures in order that the following wastes are not accepted in a landfill:
liquid waste;
waste which, in the conditions of landfill, is explosive, corrosive, oxidising, highly flammable or flammable, as defined in Annex III to Directive 91/689/EEC;
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;
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 bicylce tyres and tyres with an outside diameter above 1 400 mm);
any other type of waste which does not fulfil the acceptance criteria determined in accordance with Annex II;
waste that has been separately collected for preparing for re-use and recycling pursuant to Article 11(1) of Directive 2008/98/EC and Article 22 of that Directive, with the exception of waste resulting from subsequent treatment operations of the separately collected waste for which landfilling delivers the best environmental outcome in accordance with Article 4 of that Directive.
Member States shall include information on the measures taken pursuant to this paragraph in the waste management plans referred to in Article 28 of Directive 2008/98/EC, or in other strategic documents covering the entire territory of the Member State concerned.
A Member State may postpone the deadline for attaining the target referred to in paragraph 5 by up to five years provided that that Member State:
landfilled more than 60 % of its municipal waste generated in 2013 as reported under the Joint Questionnaire of the OECD and Eurostat; and
at the latest 24 months before the deadline laid down in paragraph 5 of this Article, notifies the Commission of its intention to postpone the deadline and submits an implementation plan in accordance with Annex IV to this Directive. That plan may be combined with an implementation plan submitted according to point (b) of Article 11(3) of Directive 2008/98/EC.
Article 5a
Rules on the calculation of the attainment of the targets
For the purpose of calculating whether the targets laid down in Article 5(5) and (6) have been attained:
the weight of the municipal waste generated and directed to landfilling shall be calculated in a given calendar year;
the weight of waste resulting from treatment operations prior to recycling or other recovery of municipal waste, such as sorting or mechanical biological treatment, which is subsequently landfilled shall be included in the weight of municipal waste reported as landfilled;
the weight of municipal waste that enters incineration disposal operations and the weight of waste produced in the stabilisation operations of the biodegradable fraction of municipal waste in order to be subsequently landfilled shall be reported as landfilled;
the weight of waste produced during recycling or other recovery operations of municipal waste which is subsequently landfilled shall not be included in the weight of municipal waste reported as landfilled.
Article 5b
Early warning report
The reports referred to in paragraph 1 shall include the following:
an estimation of the attainment of the targets by each Member State;
a list of Member States at risk of not attaining the targets within the respective deadlines accompanied by appropriate recommendations for the Member States concerned;
examples of best practices that are used throughout the Union which could provide guidance for progressing towards attaining the targets.
Article 5c
Exchange of information and best practices
The Commission shall organise a regular exchange of information and of best practices among Member States, including, where appropriate, with regional and local authorities, on the practical implementation of the requirements of this Directive.
Article 6
Waste to be accepted in the different classes of landfill
Member States shall take measures in order that:
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.
Member States shall ensure that measures taken in accordance with this point do not compromise the achievement of the objectives of Directive 2008/98/EC, notably on the waste hierarchy and on the increase of preparing for re-use and recycling as set out in Article 11 of that Directive;
only hazardous waste that fulfils the criteria set out in accordance with Annex II is assigned to a hazardous landfill;
landfill for non-hazardous waste may be used for:
municipal waste;
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;
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 hazarouds wastes shall not be deposited in cells destined for biodegradable non-hazardous waste,
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:
the identity of the applicant and of the operator when they are different entities;
the description of the types and total quantity of waste to be deposited;
the proposed capacity of the disposal site;
the description of the site, including its hydrogeological and geological characteristics;
the proposed methods for pollution prevention and abatement;
the proposed operation, monitoring and control plan;
the proposed plan for the closure and after-care procedures;
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 private projects on the environment ( 3 ), the information provided by the developer in accordance with Article 5 of that Directive;
the financial security by the applicant, or any other equivalent provision, as required under Article 8(a)(iv) of this Directive.
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.
Article 8
Conditions of the permit
Member States shall take measures in order that:
the competent authority does not issue a landfill permit unless it is satisfied that:
without prejudice to Article 3(4) and (5), the landfill project complies with all the relevant requirements of this Directive, including the Annexes;
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;
the landfill shall be operated in such a manner that the necessary measures are taken to prevent accidents and limit their consequences;
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 after-care 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 after-care 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;
the landfill project is in line with the relevant waste management plan or plans referred to in Article 7 of Directive 75/442/EEC;
prior to the commencement of disposal operations, the competent authority shall inspect the site in order to ensure that it complies with the relevant conditions of the permit. This will not reduce in any way the responsibility of the operator under the conditions of the permit.
Article 9
Content of the permit
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:
the class of the landfill;
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 after-care 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 its equivalent referred to in Article 8(a)(iv), and the estimated costs of the closure and after-care 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. Subject to the requirements of Council Directive 90/313/EEC of 7 June 1990 on the freedom of access to information on the environment ( 4 ) Member States shall ensure transparency in the collection and use of any necessary cost information.
Article 11
Waste acceptance procedures
Member States shall take measures in order that prior to accepting the waste at the landfill site:
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 appropraite 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;
the following reception procedures are respected by the operator:
the operator of the landfill shall always provide written acknowledgement of receipt of each delivery acepted on the site;
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.
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:
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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:
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 to the competent authorities for the purpose of demonstrating compliance with permit conditions and increasing the knowledge on waste behaviour in the landfills;
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 after-care procedures
Member States shall take measures in order that, in accordance, where appropriate, with the permit:
a landfill or part of it shall start the closure procedure:
when the relevant conditions stated in the permit are met; or
under the authorisation of the competent authority, at the request of the operator; or
by reasoned decision of the competent authority;
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;
after a landfill has been definitely closed, the operator shall be responsible for its maintenance, monitoring and control in the after-care 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;
for as long as the competent authority considers that a landfill is likely to cause a hazard to the environment and without prejudice to any Community or national legislation as regards liability of the waste holder, 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:
with 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 will be needed in order to comply with the requirements of this Directive with the exception of the requirements in Annex I, point 1;
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 Article 7(g) and 13, sites which have not been granted, in accordance with Article 8, a permit to continue to operate;
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);
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;
within three years after the date laid down in Article 18(1), Article 6 shall apply to landfills for hazardous waste.
Article 15
Reporting
They shall report the data electronically within 18 months of the end of the reporting year for which the data are collected. The data shall be reported in the format established by the Commission in accordance with paragraph 5 of this Article.
The first reporting period on the implementation of Article 5(5) and (6) shall start in the first full calendar year after the adoption of the implementing act that establishes the format for reporting, in accordance with paragraph 5 of this Article, and shall cover the data for that reporting period.
Article 15a
Instruments to promote a shift to a more circular economy
In order to contribute to the objectives laid down in this Directive, Member States shall make use of economic instruments and other measures to provide incentives for the application of the waste hierarchy. Such instruments and measures may include those indicated in Annex IVa to Directive 2008/98/EC or other appropriate instruments and measures.
Article 15b
Determination of the permeability coefficient for landfills
The Commission shall adopt implementing acts to lay down 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. Those implementing acts shall be adopted in accordance with the examination procedure referred to in Article 17(2).
Article 15c
Union standard for sampling of waste
The Commission shall adopt implementing acts to develop a standard for sampling of waste. Those implementing acts shall be adopted in accordance with the examination procedure referred to in Article 17(2). Until those implementing acts have been adopted, the Member States may apply national standards and procedures.
Article 16
Review of the Annexes
The Commission shall keep the Annexes under review and, where necessary, it shall make appropriate legislative proposals.
Article 17
Committee procedure
Where the committee delivers no opinion, the Commission shall not adopt the draft implementing act and the third subparagraph of Article 5(4) of Regulation (EU) No 182/2011 shall apply.
Article 18
Transposition
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.
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.
ANNEX I
GENERAL REGUIREMENTS FOR ALL CLASSES OF LANDFILLS
1. Location
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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 nature or cultural patrimony in the area. |
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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:
The above provisions may not apply to landfills for inert waste.
3. Protection of soil and water
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3.1. |
A landfill must be situated and designed so as to meet the necessary conditions for preventing pollution of the soil, groundwater or 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 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. |
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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:
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landfill for hazardous waste: K ≤ 1,0 × 10- 9 m/s; thickness ≥ 5 m,
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landfill for non-hazardous waste: K ≤ 1,0 × 10- 9 m/s; thickness ≥ 1 m,
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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 artificially and reinforced by other means giving equivalent protection. An artificially established geological barrier should be no less than 0,5 metres thick. |
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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
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 leachate formation is necessary, a surface sealing may be prescribed. Recommendations for the surface sealing are as follows:
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3.4. |
If, on the basis of an assessment of environmental risks taking into account, in particular, Directive 80/68/EEC ( 7 ), 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 above may be reduced accordingly. In the case of landfills for inert waste these requirements may be adapted by national legislation. |
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4. Gas control
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4.1. |
Appropriate measures shall be taken in order to control the accumulation and migration of landfill gas (Annex III). |
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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. |
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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. |
5. Nuisances and hazards
Measures shall be taken to minimise nuisances and hazards arising from the landfill through:
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.
8. Temporary storage of metallic mercury
For the purposes of temporary storage for more than 1 year of metallic mercury, the following requirements shall apply:
ANNEX II
WASTE ACCEPTANCE CRITERIA AND PROCEDURES
1. Introduction
This Annex describes:
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 refuses at each class of landfill, or defined 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:
Examples of waste property-based criteria are:
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 simpler 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 a 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 to temporarily from testing at Level 1. This may be due to impracticability to 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.
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.
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6. Specific requirements for metallic mercury
For the purposes of temporary storage for more than 1 year of metallic mercury, the following requirements shall apply:
Composition of the mercury
Metallic mercury shall comply with the following specifications:
Containment
Containers used for the storage of metallic mercury shall be corrosion- and shock-resistant. Welds shall therefore be avoided. The containers shall comply in particular with the following specifications:
The maximum filling ratio of the container shall be 80 % by volume to ensure that sufficient ullage is available and neither leakage nor permanent distortion of the container can occur as a result of an expansion of the liquid due to high temperature.
Acceptance procedures
Only containers with a certificate complying with the requirements set out in this Section shall be accepted.
Acceptance procedures shall comply with the following:
Certificate
The certificate indicated in subsection C shall include the following elements:
Certificates shall be issued by the producer of the waste or, in default, by the person responsible for its management.
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:
2. Meteorological data
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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 |
After-care phase |
|
1.1. Volume of precipitation |
daily |
daily, added to monthly values |
|
1.2. Temperature (min., max., 14.00 h CET) |
daily |
monthly average |
|
1.3. Direction and force of prevailing wind |
daily |
not required |
|
1.4. Evaporation (lysimeter) (1) |
daily |
daily, added to monthly values |
|
1.5. Atmospheric humidity (14.00 h CET) |
daily |
monthly average |
|
(1)
Or through other suitable methods. |
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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 is 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. For leachate and water, a sample, representative of the average composition, shall be taken for monitoring.
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.
|
|
Operating phase |
After-care phase (3) |
|
2.1. Leachate volume |
every six months |
|
|
2.2. Leachate composition (2) |
quarterly (3) |
every six months |
|
2.3. Volume and composition of surface water (7) |
quarterly (3) |
every six months |
|
2.4. Potential gas emissions and atmospheric pressure (4)(CH4, CO2, O2, H2S, H2 etc.) |
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)
Thease 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)). |
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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 ( 8 ).
|
|
Operation phase |
After-care phase |
|
Level of groundwater |
every six months (1) |
every six months (1) |
|
Groundwater composition |
||
|
(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. |
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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 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 body |
yearly |
yearly reading |
|
(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. |
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6. Specific requirements for metallic mercury
For the purposes of temporary storage for more than 1 year of metallic mercury, the following requirements shall apply:
Monitoring, inspection and emergency requirements
A continuous mercury vapour monitoring system with a sensitivity of at least 0,02 mg mercury/m3 shall be installed in the storage site. Sensors shall be positioned at ground level and head level. This shall include a visual and acoustic alert system. The system shall be maintained annually.
The storage site and containers shall be visually inspected by an authorised person at least once a month. Where leaks are detected, the operator shall immediately take all necessary action to avoid any emission of mercury to the environment and restore the safety of the storage of the mercury. Any leaks shall be considered to have significant adverse environmental effects as referred to in Article 12(b).
Emergency plans and adequate protective equipment suitable for handling metallic mercury shall be available on site.
Record keeping
All documents containing the information referred to in Section 6 of Annex II and in point A of this Section, including the certificate accompanying the container, as well as records concerning the destocking and dispatch of the metallic mercury after its temporary storage and the destination and intended treatment shall be kept for at least 3 years after the termination of the storage.
ANNEX IV
IMPLEMENTATION PLAN TO BE SUBMITTED PURSUANT TO ARTICLE 5(6)
The implementation plan to be submitted pursuant to Article 5(6) shall contain the following:
assessment of the past, current and projected rates of recycling, landfilling and other treatment of municipal waste and the streams of which it is composed;
assessment of the implementation of waste management plans and waste prevention programmes in place pursuant to Articles 28 and 29 of Directive 2008/98/EC;
reasons for which the Member State considers that it might not be able to attain the relevant target laid down in Article 5(5) within the deadline set therein and an assessment of the time extension necessary to meet that target;
measures necessary to attain the targets set out in Article 5(8) of this Directive applicable to the Member State during the time extension, including appropriate economic instruments and other measures to provide incentives for the application of the waste hierarchy as set out in Article 4(1) of, and Annex IVa to, Directive 2008/98/EC;
a timetable for the implementation of the measures identified in point 4, determination of the body competent for their implementation and an assessment of their individual contribution to attaining the targets applicable in the event of a time extension;
information on funding for waste management in line with the polluter-pays principle;
measures to improve data quality, as appropriate, with a view to better planning and monitoring performance in waste management.
( 1 ) Directive 2008/98/EC of the European Parliament and of the Council of 19 November 2008 on waste and repealing certain Directives (OJ L 312, 22.11.2008, p. 3).
( 2 ) Regulation (EC) No 1013/2006 of the European Parliament and of the Council of 14 June 2006 on shipments of waste (OJ L 190, 12.7.2006, p. 1).
( 3 ) OJ L 175, 5.7.1985, p. 40. Directive as amended by Directive 97/11/EC (OJ L 73, 14.3.1997, p. 5).
( 4 ) OJ L 158, 23.6.1990, p. 56.
( 5 ) 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).
( 6 ) Regulation (EU) No 182/2011 of the European Parliament and of the Council of 16 February 2011 laying down the rules and general principles concerning mechanisms for control by Member States of the Commission’s exercise of implementing powers (OJ L 55, 28.2.2011, p. 13).
( 7 ) 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).
( 8 ) Recommended parameters: ph, TOC, phenols, heavy metals, fluoride, AS, oil/hydrocarbons.
